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HomeMy WebLinkAboutO-2892 - Adopts 2011 sewer comprehensive plan (Special)CITY OF MARYSVILLE Marysville, Washington ORDINANCE NO.J.-~qd- AN ORDINANCE OF THE CITY OF MARYSVILLE, WASHINGTON, ADOPTING THE 2011 SEWER COMPREHENSIVE PLAN PURSUANT TO CHAPTER 173-240 WAC; AND DIRECTING THAT SAID PLAN BE DOCKETED IN THE 2012 GMA COMPREHENSIVE PLAN DOCKET PROCESS TO BE CONSIDERED FOR ADOPTION AS A PART OF THE PUBLIC FACILITIES AND SERVICES ELEMENT OF THE MARYSVILLE GROWTH MANAGEMENT COMPREHENSIVE PLAN. WHEREAS, before constructing or modifying domestic wastewater facilities, engineering reports and plans and specifications for the project must be submitted to and approved by the Washington State Department of Ecology, pursuant to Chapter 173-240 WAC; and WHEREAS, the City of Marysville submitted the 2011 Sewer Comprehensive Plan to the Washington State Department of Ecology for review and approval as required by WAC 173-240-050; and WHEREAS, the City of Marysville's existing Sewer Comprehensive Plan was approved by Ordinance No. 2569 on April 25, 2005; and WHEREAS, the 2011 Sewer Comprehensive Plan identifies the planning needs and necessary capital improvements for the City's wastewater collection, transmission, treatment and disposal for a 20-year horizon commencing in 2011; and WHEREAS, the proposed 2011 Sewer Comprehensive Plan is based on and complies with the objectives and requirements of the Washington State Growth Management Act (GMA) RCW 36.70A; and WHEREAS, the City has submitted the 2011 Sewer Comprehensive Plan to the State of Washington Department of Commerce for 60-day review in accordance with RCW 36.70A.106; and WHEREAS, following public comment and notice, the City issued Addendum No. 21 to the Final Environmental Impact Statement (FEIS) for the City of Marysville Comprehensive Plan, on January 23, 2012, which Addendum No. 21 addresses the environmental impacts of the 2011 Sewer Comprehensive Plan; and WHEREAS, for the purpose of complying with the requirements of WAC 173-240 and RCW 36.70A.070, the Marysville Planning Commission held a public workshop on January 24, 2012, and a public hearing on February 28, 2012, to accept public comment and to review the 2011 Sewer Comprehensive Plan; and WHEREAS, on April 9, 2012 the Marysville City Council reviewed the Planning Commission's recommendation relating to the adoption of the 2011 Sewer Comprehensive Plan; NOW, THEREFORE, THE CITY COUNCIL OF THE CITY OF MARYSVILLE, WASHINGTON DO ORDAIN AS FOLLOWS: Section 1. The document entitled "2011 City of Marysville Sewer Comprehensive Plan," as set forth in the attached Exhibit A, is hereby adopted pursuant to Chapter 173­ 240 WAC. A copy of said Plan shall be made available for inspection and review at the office of the City Clerk and the office of Community Development. Section 2. The Director of Community Development is hereby directed to include the 2011 Sewer Comprehensive Plan in the 2012 GMA Comprehensive Plan Docket process to be considered for adoption as part of the Public Facilities and Services Element of the Marysville Comprehensive Plan. Section 3. Upon adoption for both the purposes of WAC 173-240 and RCW 36.70A.070, the "2011 City of Marysville Sewer Comprehensive Plan" adopted herein shall replace and supersede all previous Sewer Comprehensive Plans, which shall no longer be in effect. Section 4. Severability. If any section, subsection, sentence, clause, phrase or work of this ordinance should be held to be invalid or unconstitutional by a court of competent jurisdiction, such invalidity or unconstitutionality thereof shall not affect the validity or constitutionality of any other section, subsection, sentence, clause, phrase or word of this ordinance. PASSED by the City Council and APPROVED by the Mayor this Dth _-,'-----_ day of ---=D.------'irUb,--' , 2012. CITY OF MARYSVILLE BY:~~-t:s J~ NEHRING/MAY Attest: fkJ /")12/1 . By: U~ ~tj CITY LERK Approved as to form: By: ,6. . (,. W~ 'GRANT K. WEED, CITY ATTORNEY Date of Publication: 4-/[-fL Effective Date: EXHIBIT A 2011 City of Marysville Sewer Comprehensive Plan City of Marysville Sewer Comprehensive Plan November 2011 i TABLE OF CONTENTS EXECUTIVE SUMMARY INTRODUCTION ....................................................................................................E-1 SERVICE AREA DEVELOPMENT ..........................................................................E-1 EXISTING FACILITIES ..........................................................................................E-2 WASTEWATER CHARACTERISTICS AND FLOWS .................................................E-2 COLLECTION SYSTEM EVALUATION ..................................................................E-3 WASTEWATER TREATMENT EVALUATION .........................................................E-4 OPERATION AND MAINTENANCE ........................................................................E-5 CAPITAL IMPROVEMENT PLAN ...........................................................................E-5 CHAPTER 1 - INTRODUCTION WASTEWATER SYSTEM OWNERSHIP AND MANAGEMENT ................................. 1-1 PURPOSE .............................................................................................................. 1-1 SCOPE .................................................................................................................. 1-2 HISTORY OF WASTEWATER SYSTEM DEVELOPMENT ........................................ 1-3 Projects Completed Since the 2005 Comprehensive Sanitary Sewerage Plan ... 1-6 RELATED PLANNING DOCUMENTS ...................................................................... 1-7 Water System Plans ............................................................................................ 1-6 Wastewater Comprehensive/Facility Plans ........................................................ 1-6 GMA Comprehensive Plans ............................................................................... 1-6 CHAPTER 2 – PLANNING AREA INTRODUCTION .................................................................................................... 2-1 PLANNING AREA .................................................................................................. 2-1 NATURAL FEATURES OF THE STUDY AREA ........................................................ 2-1 Topography and Geography ............................................................................... 2-2 Soils and Geology .............................................................................................. 2-2 Surface Water ..................................................................................................... 2-3 Climate ............................................................................................................... 2-4 Site Sensitive Areas ............................................................................................ 2-4 WATER SYSTEM .................................................................................................. 2-6 OTHER PUBLIC UTILITIES .................................................................................. 2-9 CHAPTER 3 - LAND USE AND PLANNING CRITERIA INTRODUCTION .................................................................................................... 3-1 PLANNING PERIOD............................................................................................... 3-1 GROWTH MANAGEMENT .................................................................................... 3-1 LAND USE AND ZONING ....................................................................................... 3-2 City of Marysville .............................................................................................. 3-2 Snohomish County ............................................................................................. 3-8 POPULATION ...................................................................................................... 3-10 Existing Population .......................................................................................... 3-10 Schools ............................................................................................................. 3-11 ii Projected Future Population ............................................................................. 3-14 Neighborhood Population Planning ................................................................. 3-15 Non UGA Sewers ............................................................................................. 3-17 Sewer Connections ........................................................................................... 3-18 Current Sewer Service Area ............................................................................. 3-19 Projected Sewer Service Area Population ........................................................ 3-19 Ultimate Buildout Population ........................................................................... 3-20 CHAPTER 4 - REGULATORY REQUIREMENTS INTRODUCTION .................................................................................................... 4-1 FEDERAL AND STATE STATUTES, REGULATIONS AND PERMITS ........................ 4-1 Federal Clean Water Act .................................................................................... 4-1 Proposed EPA Capacity, Management Operation and Maintenance Regulations .................................................................................................. 4-2 Biosolids ............................................................................................................. 4-3 Federal Endangered Species Act ........................................................................ 4-3 Reclaimed Water Standards ............................................................................... 4-4 National Environmental Policy Act ................................................................... 4-5 Federal Clean Air Act......................................................................................... 4-6 STATE STATUTES, REGULATIONS AND PERMITS ................................................ 4-6 State Water Pollution Control Act ...................................................................... 4-6 Water Quality Standards for Surface Waters of the State of Washington, Chapter 173-201A WAC ........................................................................................... 4-7 State Environmental Policy Act ....................................................................... 4-13 Growth Management ........................................................................................ 4-13 Accreditation of Environmental Laboratories (WAC 173-050) ....................... 4-14 Minimal Standards for Solid Waste Handling (WAC 173-304) ...................... 4-14 Wetlands ........................................................................................................... 4-14 Shoreline Management Act .............................................................................. 4-15 Floodplain Development Permit ...................................................................... 4-15 Hydraulic Project Approval .............................................................................. 4-15 PRETREATMENT REQUIREMENTS ..................................................................... 4-15 ON-SITE SEPTIC SYSTEM REGULATIONS ......................................................... 4-16 SEWER ORDINANCES AND PLANNING POLICIES ............................................... 4-16 CITY WASTEWATER OPERATION AND MAINTENANCE STANDARDS ............... 4-17 CHAPTER 5 - EXISTING FACILITIES INTRODUCTION .................................................................................................... 5-1 WASTEWATER COLLECTION SYSTEM ................................................................ 5-1 Pressure and Gravity Sewers .............................................................................. 5-1 Pump Stations ..................................................................................................... 5-2 Wastewater Treatment Plant .............................................................................. 5-7 WWTF Design Criteria and Current Plant Loadings ......................................... 5-7 NPDES Permit ............................................................................................. 5-8 Wastewater Treatment Plant Description ......................................................... 5-10 Headworks ................................................................................................. 5-10 Influent Flow Measurement ....................................................................... 5-11 Lagoon System .......................................................................................... 5-11 Coagulation and Filtration Facilities .......................................................... 5-12 iii Ultraviolet Disinfection System ................................................................. 5-12 Effluent Pumps .......................................................................................... 5-12 Effluent Disposal ....................................................................................... 5-12 INTERLOCAL AGREEMENTS .............................................................................. 5-13 City of Arlington .............................................................................................. 5-13 Snohomish County ........................................................................................... 5-13 Tulalip Tribes ................................................................................................... 5-14 Lake Stevens Sewer District ............................................................................. 5-14 City of Everett .................................................................................................. 5-14 Mutual Aid Agreement ..................................................................................... 5-15 REFERENCES ...................................................................................................... 5-16 CHAPTER 6 - EXISTING AND PROJECTED WASTEWATER FLOWS AND CHARACTERISTICS INTRODUCTION .................................................................................................... 6-1 DEFINITION OF TERMS ........................................................................................ 6-1 Wastewater ......................................................................................................... 6-1 Domestic Wastewater ......................................................................................... 6-1 Equivalent Residential Unit (ERU) .................................................................... 6-1 Non-Residential Wastewater .............................................................................. 6-2 Infiltration ........................................................................................................... 6-2 Inflow ................................................................................................................. 6-2 Average Dry Weather Flow ............................................................................... 6-2 Average Annual Flow ........................................................................................ 6-3 Maximum Month Flow (Treatment Design Flow) ............................................. 6-3 Peak Hour Flow .................................................................................................. 6-3 Biochemical Oxygen Demand (BOD)................................................................ 6-3 Suspended Solids ................................................................................................ 6-4 Chlorine .............................................................................................................. 6-4 Ultraviolet Disinfection ...................................................................................... 6-4 Sand Filter .......................................................................................................... 6-5 Other Contaminants of Concern ......................................................................... 6-5 EXISTING WASTEWATER FLOWS AND LOADING ................................................ 6-5 Historical Wastewater Flows and Loadings at City of Marysville WWTP........ 6-6 EXISTING EQUIVALENT RESIDENTIAL UNITS (ERUS) ..................................... 6-10 WATER CONSUMPTION ..................................................................................... 6-10 Equivalent Residential Units ............................................................................ 6-11 INFILTRATION AND INFLOW .............................................................................. 6-12 I/I Analysis Using EPA Criteria ....................................................................... 6-13 Infiltration ......................................................................................................... 6-14 Inflow ............................................................................................................... 6-14 Flow Monitoring .............................................................................................. 6-14 I/I Summary ...................................................................................................... 6-15 PROJECTED SEWER SERVICE AREA POPULATION, ERUS AND FLOWS ........... 6-15 EXISTING AND PROJECTED INFLUENT BOD5 AND TSS LOADING ................... 6-17 Existing BOD5 Loading .................................................................................... 6-17 Existing Total Suspended Solids Loading ........................................................ 6-17 Projected Wastewater Loadings ....................................................................... 6-17 INDUSTRIAL WASTEWATER .............................................................................. 6-18 iv REFERENCES ...................................................................................................... 6-21 CHAPTER 7 - COLLECTION SYSTEM EVALUATION INTRODUCTION .................................................................................................... 7-1 Hydraulic Model ................................................................................................ 7-1 Model Layers ...................................................................................................... 7-2 Record Drawings ................................................................................................ 7-3 Interpolated Manholes ........................................................................................ 7-3 Surveyed Manholes ............................................................................................ 7-3 Pump Stations ..................................................................................................... 7-4 Basins ................................................................................................................. 7-4 Hydraulic Modeling Analysis ............................................................................ 7-5 YEAR 2011 HYDRAULIC MODELING ANALYSIS ................................................. 7-6 Existing Population ............................................................................................ 7-6 Schools ............................................................................................................... 7-7 Commercial/Industrial ........................................................................................ 7-7 Inflation/Inflow .................................................................................................. 7-8 Year 2011 Hydraulic Modeling Data ................................................................. 7-8 YEAR 2017 HYDRAULIC MODELING ANALYSIS ................................................. 7-8 YEAR 2031 HYDRAULIC MODELING ANALYSIS ................................................. 7-9 YEAR 2011, 2017, AND 2031 MODELING RESULTS WITHOUT IMPROVEMENTS7-10 YEAR 2011, 2017, AND 2031 MODELING RESULTS WITH IMPROVEMENTS ..... 7-13 BUILDOUT HYDRAULIC MODELING ANALYSIS ................................................ 7-14 BUILDOUT MODELING RESULTS ....................................................................... 7-15 OTHER PIPELINE DEFICIENCIES ....................................................................... 7-16 PUMP STATION CAPACITY ANALYSIS ............................................................... 7-16 RECOMMENDED PUMP STATION IMPROVEMENTS ........................................... 7-17 FORCE MAIN CAPACITY EVALUATION ............................................................. 7-20 SUMMARY OF COLLECTION SYSTEM IMPROVEMENTS .................................... 7-22 CHAPTER 8 - WASTEWATER TREATMENT PLANT ANALYSIS INTRODUCTION .................................................................................................... 8-1 Capacity Evaluation at Design Flows and Loadings .......................................... 8-2 HEADWORKS ........................................................................................................ 8-2 Influent Screw Pumps ........................................................................................ 8-2 Influent Screening .............................................................................................. 8-3 Influent Flow Measurement ............................................................................... 8-3 LAGOON SYSTEM ................................................................................................. 8-3 EFFLUENT FILTRATION ....................................................................................... 8-4 DISINFECTION ...................................................................................................... 8-5 EFFLUENT DISPOSAL ........................................................................................... 8-6 EVALUATION OF WATER RECLAMATION AND REUSE ....................................... 8-7 Potential for Reuse ............................................................................................. 8-7 Industrial Cooling Water .................................................................................... 8-7 Irrigation/Landscaping Use ................................................................................ 8-8 v Fire Protection .................................................................................................... 8-8 Ground Water Recharge ..................................................................................... 8-8 Other Possibilities .............................................................................................. 8-8 Offsets to Existing Water Rights ........................................................................ 8-8 Wetlands Flow Augmentation ............................................................................ 8-9 CONCEPTUAL DESIGN AND COST ESTIMATE ..................................................... 8-9 Irrigation Demands ............................................................................................. 8-9 Production of Reclaimed Water ....................................................................... 8-10 Coagulation and Filtration ................................................................................ 8-10 UV Disinfection System ................................................................................... 8-11 Alarms and Telemetry ...................................................................................... 8-11 Distribution and Storage ................................................................................... 8-11 ECONOMIC FEASIBILITY OF REUSE .................................................................. 8-12 WWTP RECOMMENDED IMPROVEMENTS ....................................................... 8-15 CHAPTER 9 - BIOSOLIDS MANAGEMENT GENERAL ............................................................................................................. 9-1 BIOSOLIDS REGULATIONS ................................................................................... 9-1 40 CFR Part 503 ................................................................................................. 9-1 WAC-173-308 Biosolids Management .............................................................. 9-1 BIOSOLIDS QUALITY AND CHARACTERISTICS ................................................... 9-5 BIOSOLIDS MANAGEMENT .................................................................................. 9-9 CHAPTER 10 - OPERATION AND MAINTENANCE INTRODUCTION .................................................................................................. 10-1 RESPONSIBILITY AND AUTHORITY ................................................................... 10-1 Personnel Certification ..................................................................................... 10-2 Full-Time Employees (FTEs) ........................................................................... 10-2 NORMAL SYSTEM OPERATION .......................................................................... 10-3 Routine and Preventative Maintenance Criteria ............................................... 10-3 Pump Station and Generator Maintenance ....................................................... 10-4 Gravity Sewers and Manholes .......................................................................... 10-7 Pipeline Cleaning ............................................................................................. 10-7 Hydraulic Cleaning........................................................................................... 10-7 Mechanical Cleaning ........................................................................................ 10-8 Chemical Cleaning ........................................................................................... 10-8 Video Inspection .............................................................................................. 10-8 Cleaning and Inspection Standards .................................................................. 10-9 Current Staffing Needs ..................................................................................... 10-9 Future Staffing Needs ....................................................................................... 10-9 CAPACITY MANAGEMENT OPERATION AND MAINTENANCE (CMOM) AND FUTURE STAFFING NEEDS ......................................................................... 10-10 Capacity Management Operation and Maintenance (CMOM) ...................... 10-10 CAPACITY MANAGEMENT OPERATION AND MAINTENANCE (CMOM) DRAFT REQUIREMENTS ......................................................................................... 10-11 SAFETY ............................................................................................................. 10-13 Confined Spaces ............................................................................................. 10-13 Electrical and Mechanical Equipment ............................................................ 10-14 vi Fire Hazards ................................................................................................... 10-15 Health/Safety .................................................................................................. 10-15 EMERGENCY RESPONSE .................................................................................. 10-15 MAINTENANCE PERSONNEL QUALIFICATIONS .............................................. 10-17 CHAPTER 11 - CAPITAL IMPROVEMENT PLAN INTRODUCTION .................................................................................................. 11-1 PROPOSED SYSTEM IMPROVEMENTS FROM 2011 TO 2017 .............................. 11-2 Sanitary Sewer Mains ....................................................................................... 11-2 Pump Stations ................................................................................................... 11-4 WWTP Improvements ...................................................................................... 11-5 General System Improvements ........................................................................ 11-7 TOTAL 6-YEAR CIP .......................................................................................... 11-7 PROPOSED SYSTEM IMPROVEMENTS FROM 2018 TO 2031 ............................ 11-10 Sanitary Sewer Mains ..................................................................................... 11-10 Pump Stations ................................................................................................. 11-11 WWTP Improvements .................................................................................... 11-12 General System Improvements ...................................................................... 11-13 TOTAL 20-YEAR CIP ...................................................................................... 11-14 CHAPTER 12 - FINANCING INTRODUCTION .................................................................................................. 12-1 WASTEWATER RATES AND CHARGES ............................................................... 12-1 FINANCIAL STATUS OF THE EXISTING SYSTEM ................................................ 12-3 Historical Operating Cash Flows ..................................................................... 12-3 Projected Operating Cash Flows ...................................................................... 12-4 CAPITAL FUNDS AVAILABLE FOR FUTURE IMPROVEMENTS ........................... 12-6 APPENDICES Appendix A NPDES Permit No. WA-002249-7 Appendix B City of Marysville Agreements Appendix C Pump Station Inventory Appendix D Land Use Data/Loading Tables Appendix E Hydraulic Model Results Appendix F Effluent TSS and CBOD Trending Charts Appendix G CMOM Checklist Appendix H Cost Estimates Appendix I SEPA Checklist EXHIBITS Exhibit I - Existing Sewer System and Land Use/Subareas Exhibit II – Sewer System Aerial Exhibit III – Modeled Sewer Lines, Manhole ID’s and Basins Exhibit IV – Pipe ID and Capacity Deficiencies (Model Runs 2011, 2017, and 2031) Exhibit V – Modeled Sewer Lines with Improvements and Buildout Conditions Exhibit VI – Pipe ID and Pipeline Velocity Deficiencies (2011) vii LIST OF TABLES No. Table Page E-1 Projected Sewer Service Population Summary ............................................................... E-2 E-2 Current and Projected Flows and Loadings ..................................................................... E-3 E-3 6-Year Capital Improvement Plan ................................................................................... E-7 1-1 City of Marysville Sewer Service Connection Growth ................................................... 1-5 1-2 Projects Completed Since 2005 Sanitary Sewerage Plan CIP ......................................... 1-6 2-1 Planning Area Acreage .................................................................................................... 2-1 2-2 2009 to 2014 Water System Capacity Improvements ..................................................... 2-8 3-1 City of Marysville Zoning Designations ......................................................................... 3-3 3-2 Snohomish County Marysville UPA Zoning Designations ............................................. 3-8 3-3 UGA land Use Designation Acreage from Marysville Comprehensive Plan 2011 ....... 3-10 3-4 2010 Population and Housing Units Corporate Boundary ............................................ 3-11 3-5 Marysville School District Student and Staff Population: 2002-2010 .......................... 3-12 3-6 Lakewood School District Student and Staff Population: 2010 .................................... 3-13 3-7 Projected Population 2010 to 2031................................................................................ 3-14 3-8 UGA Additional Population Capacity ........................................................................... 3-16 3-9 2011 Sewer Service Connections .................................................................................. 3-18 3-10 Marysville 2011 Estimated Sewer Service Population.................................................. 3-19 3-11 Projected Sewer Service Population Summary ............................................................. 3-20 3-12 2031 Capacity Population ............................................................................................. 3-22 4-1 Water Quality Criteria for the Salmon and Trout Spawning, Non-Core Rearing and Migration Use .................................................................................................................. 4-9 4-2 Water Quality Criteria for the Freshwater Primary Contact Recreational use .............. 4-10 4-3 City of Marysville 2005 NPDES/TMDL Seasonal Effluent Limits .............................. 4-13 4-4 Title 14 MMC Water and Sewers .................................................................................. 4-17 5-1 Trunk Sewer Service Area .............................................................................................. 5-1 5-2 Gravity Sewer Inventory ................................................................................................. 5-3 5-3 Inventory of Force Main .................................................................................................. 5-4 5-4 Inventory of Sewage Pump Stations ................................................................................ 5-5 5-5 Wastewater Treatment Plant Design Flows and Loading ............................................... 5-9 5-6 Wastewater Treatment Plant NPDES Permit Limits Low Flow Season (July - October) ............................................................................................................... 5-9 5-7 Wastewater Treatment Plant NPDES Permit Limits High Flow Season (November through June) ................................................................................................ 5-9 5-8 Wastewater Treatment Plant NPDES Permit Facility Loading Criteria .......................... 5-9 5-9 Lagoon System Design Criteria..................................................................................... 5-11 6-1 Historical WWTP Influent Flows (2006 - 2010) ............................................................. 6-6 6-2 Summary of Discharge Monitoring Reports (DMRs) WWTP Influent and Effluent Monthly Averages ............................................................................................. 6-7 6-3 WWTP Flow and Loading Summary .............................................................................. 6-9 6-4 2010 Annual Average Water Use by Customer Class ................................................... 6-10 6-5 Major Water Consumers for 2010 ................................................................................. 6-11 6-6 Current Wastewater ERUs ............................................................................................ 6-12 6-7 Estimated Infiltration and Inflow .................................................................................. 6-13 6-8 Per Capita Infiltration and Inflow Based on EPA Criteria ............................................ 6-14 6-9 Current and Projected Future Wastewater ERUs and Flows ......................................... 6-16 6-10 Current and Projected WWTP Loadings ....................................................................... 6-18 6-11 Industrial Wastewater Producers - 2011 ....................................................................... 6-19 viii 7-1 Collection System Information........................................................................................ 7-2 7-2 Peaking Factors ............................................................................................................... 7-5 7-3 2011 Population ............................................................................................................... 7-6 7-4 2017 Population ............................................................................................................... 7-8 7-5 2031 Population ............................................................................................................... 7-9 7-6 Modeled Peak Flows vs. Projected Peak Flows ............................................................ 7-10 7-7 Pipeline Capacity Deficiencies for 2011, 2017, and 2031 without Improvements ....... 7-11 7-8 Buildout Population ....................................................................................................... 7-15 7-9 “Developer Type” Pump Station Capacity Analysis ..................................................... 7-18 7-10 Main Pump Station Capacity Analysis .......................................................................... 7-19 7-11 Force Main Capacity Evaluation ................................................................................... 7-21 7-12 Collection System and Pump Station Capital Improvement Projects ........................... 7-23 8-1 NPDES Effluent Concentration Limitations ................................................................... 8-1 8-2 Comparison of Phase 2 Capacity Rating to Current and Projected WWTP Flows and Loadings ................................................................................................................... 8-2 8-3 Sources and Supply for the Marysville Coordinated Service Area ................................. 8-9 8-4 Potential Irrigation Use for Reclaimed Water ............................................................... 8-10 8-5 Capital Cost Estimates for Water Reuse System ........................................................... 8-13 8-6 Annual O&M Cost Estimate for Water Reuse System.................................................. 8-13 8-7 Comparison of Reclaimed Water and Potable Water Costs .......................................... 8-14 8-8 Recommended WWTP Improvements and Actions ...................................................... 8-16 9-1 Pollutant and Other Characteristics in Biosolids from Marysville WWTP (1994 Sampling Data) ..................................................................................................... 9-6 9-2 Pollutant and Other Characteristics in Biosolids from Marysville WWTP (2002 Sampling Data) ..................................................................................................... 9-7 9-3 Biosolids Accumulation Rates ...................................................................................... 9-12 9-4 Cost Estimate for Contract Land Application of Class “B” Biosolids .......................... 9-13 10-1 2011 Wastewater Treatment Plant Personnel Certifications ......................................... 10-2 10-2 2010 Operation and Maintenance Budget for Collection System ................................. 10-3 10-3 Preventative Maintenance Schedule .............................................................................. 10-4 10-4 Pump Station Maintenance Schedule ............................................................................ 10-5 10-5 Pump Station Inspection and Maintenance Staffing Requirements .............................. 10-6 10-6 Staffing Requirements for Inspection and Cleaning ..................................................... 10-9 10-7 Estimation of Future Staffing Needs Collection System ............................................. 10-10 10-8 Emergency Response Actions for Pump Stations ....................................................... 10-16 10-9 Emergency Response Actions for Forcemains ............................................................ 10-16 10-10 Emergency Response Actions for Gravity Sewer ....................................................... 10-17 11-1 6-year Capital Improvements Plan ................................................................................ 11-8 11-2 Capital Improvements Plan 2018 - 2031 ..................................................................... 11-14 12-1 Wastewater Bi-Monthly Rates ...................................................................................... 12-2 12-2 Existing General Facility Charges ................................................................................. 12-3 12-3 Historical Wastewater Revenues and Expenses ............................................................ 12-4 12-4 Projected Operating Cash Flows ................................................................................... 12-5 12-5 Projected Funds Available for Capital Funding ............................................................ 12-7 ix LIST OF FIGURES No. Table Following Page E-1 Sewer Basin Area and Planning Areas ............................................................................ E-1 E-2 Six Year CIP .................................................................................................................... E-6 1-1 Location Map .................................................................................................................. 1-2 2-1 Adjacent Jurisdictions ..................................................................................................... 2-1 2-2 Corporate Boundaries and Planning Areas ...................................................................... 2-1 2-3 Area Topography ............................................................................................................. 2-2 2-4 Area Soils ........................................................................................................................ 2-2 2-5 Site Sensitive Areas ......................................................................................................... 2-4 2-6 Watersheds ...................................................................................................................... 2-5 3-1 Existing Zoning ............................................................................................................... 3-2 3-2 Census Tracts ................................................................................................................ 3-10 3-3 Marysville Neighborhoods ............................................................................................ 3-15 3-4 Future Sewer Growth .................................................................................................... 3-21 5-1 Collection System............................................................................................................ 5-1 5-2 WWTP Site Layout ....................................................................................................... 5-10 5-3 Interlocal Agreements ................................................................................................... 5-15 6-1 Average and Peak Day WWTF Influent Flow ................................................................ 6-6 6-2 Monthly Average Influent BOD & TSS .......................................................................... 6-6 6-3 Monthly Average Effluent CBOD5 Concentrations ........................................................ 6-6 6-4 Monthly Average CBOD5 Effluent Loading ................................................................... 6-6 7-1 Modeled Sewer Lines ...................................................................................................... 7-2 7-2 Neighborhood Planning ................................................................................................... 7-5 7-3 Model Inputs.................................................................................................................... 7-5 7-4 Model Results (2011) .........................................................................................Appendix E 7-5 Model Results (2017) .........................................................................................Appendix E 7-6 Model Results (2031) .........................................................................................Appendix E 7-7 Model Results (Buildout w/Improvements) .......................................................Appendix E 8-1 Hydraulic Profile ............................................................................................................. 8-6 8-2 Proposed Reclaimed Water system ............................................................................... 8-14 10-1 Organization Chart ........................................................................................................ 10-1 11-1 Six Year CIP .................................................................................................................. 11-1 LIST OF ABBREVIATIONS AAF average annual flow ADWF average dry weather flow AKART All known, available, and reasonable technologies BOD5 5-day biochemical oxygen demand CBOD5 5-day Carboneous Biochemical Oxygen Demand CFR Code of Federal Regulations cfu colony forming units CIP Capital Improvement Plan City City of Marysville CMOM Capacity Management Operation Maintenance CWA Clean Water Act DI ductile iron DMR discharge monitoring reports DNS determination of non-significance DOH Washington State Department of Health DU Dwelling Unit Ecology Washington State Department of Ecology EIS Environmental Impact Statement EPA Environmental Protection Agency ERU Equivalent Residential Unit ESA Endangered Species Act FTE full time equivalent GIS Global Information System GMA Growth Management Act gpcd gallons per capita per day gpd gallons per day gpd/acre Gallons per day - per acre gpm gallons per minute gpm/sf gallons per minute per square foot HDPE high density polyethylene hp horsepower hpa Hydraulic project approval HRT hydraulic residence time I/I infiltration and inflow kW kilowatt kWhr kilowatt hour lb. pounds lb./day pounds per day lb/sf/day pounds per square foot per day lf linear foot LS lump sum MCRI Municipal, residential, commercial and industrial development MCRT Mean cell residence time MDF maximum daily flow LIST OF ABBREVIATIONS - continued MG million gallons mgd million gallons per day mg/L milligrams per liter MH manhole mL milliliters MLSS Mixed liquor suspended solids MMC Marysville Municipal Code MMF maximum monthly flow mpn most probable number NA not applicable NEPA National Environmental Policy Act NMFS National Marine Fisheries Service NO3-N nitrate - nitrogen NPDES National Pollutant Discharge Elimination System NTU nephelometric turbidity units O&M operations and maintenance pH negative log hydronium ion concentration PHF peak hour flow POTW Publicly owned treatment works PPC Persons per Capita psi pounds per square inch PSRP process to significantly reduce pathogens PVC polyvinyl chloride RDI/I Rain dependent I/I RAS return activated sludge RCW Revised Code of Washington RUSA Rural Utility Service Area scfm standard cubic feet per minute SEPA State Environmental Policy Act SRT Sludge Retention Time TKN total Kjehldahl nitrogen TMDL total maximum daily load TSS total suspended solids UGA Urban Growth Area ULID Utility Local Improvement District UPA Ultimate Planning Area USA Utility Service Area UV Ultraviolet Radiation USFWS United States Fish and Wildlife Service uW/s*cm2 microwatts per second centimeter squared VFD variable frequency drive WAC Washington Administrative Code WAS waste activated sludge WSDF&W Washington State Department of Fish Wildlife WSDOT Washington State Department of Transportation WWTP wastewater treatment plant City of Marysville E-1 Sewer Comprehensive Plan November 2011 EXECUTIVE SUMMARY INTRODUCTION The 2011 Sewer Comprehensive Plan for the City of Marysville addresses the City’s comprehensive planning needs for wastewater collection, transmission, treatment, and disposal for the next 20 years. This Plan was prepared in accordance with the provisions of the Revised Code of Washington (RCW), Section 90.48, Water Pollution Control, Washington Administrative Code (WAC) Section 173-240-050, General Sewer Plan, and WAC 173-240-060, Engineering Report. Development of the Plan has been coordinated with the City’s Comprehensive Plan and local agreements with adjacent jurisdictions. This Plan includes discussion of general planning issues including growth management, land use, zoning, and population projections. Regulatory issues that are relevant to the planning and implementation of wastewater service improvements are discussed. The existing facilities for wastewater collection, conveyance, treatment, and biosolids handling are described and evaluated in detail. A computerized hydraulic model is used to assess the capacity of the existing collection system and to plan for future facilities. Capital improvement recommendations and an implementation schedule for these improvements are presented. SERVICE AREA DEVELOPMENT Chapter 2 provides a description of the planning area for the City of Marysville. The planning area consists of three components: the City’s corporate boundary, approximately 13,370 acres, the Urban Growth Area (UGA) covering 13,660 acres, and the ultimate planning area, approximately 24,000 acres, or 37.5 square miles. The UGA is the City’s primary planning area for locating sewers and other types of urban development. The ultimate planning area is located outside of the UGA but has the potential of inclusion in future UGA boundary adjustments. The three components of the City’s planning area are shown on Figure E-1. Chapter 3 develops population estimates for the City’s UGA and adjacent areas using information from the 2005 Marysville Comprehensive Plan and the Snohomish County Buildable Lands reports. The City’s UGA population in 2010 was approximately 60,183 and is expected to grow to 84,989 in 2031 under a moderate growth rate of 2 percent. For sewer, the City provides service to three areas outside of its UGA, a part of Arlington to the north, part of the Tulalip Tribes to the west, and Mountain View Shores also to the west. In addition, not all current residences are connected to the City’s service system. Table E-1 presents the population connected to the sewer system through 2025. The City has averaged 445 sewer connections per year between 2001 and 2005 and 353 sewer connections per year between 2006 and 2010. 16THAVE NW132ND ST NE 99TH AVE NESR 52834TH AVE NE79TH AVE NE71ST AVE NESR 92 76TH ST NE 84TH ST NE SR 980TH ST NE ASH AVE116TH ST NE SR 984TH ST NE 52NDST NESHOULTES RD132ND ST NE 108TH ST NE SR 531 67TH AVE NE SMOKEY POINT BLVDI -5 I-551ST AVE NE88TH ST NE 67TH AVE NE 51ST AVE NE I -523RDAVE NEARMARRD140TH ST NE 48TH DR NE136TH ST NE FORTY-FIVE RD3RD AVE NE44TH ST NESUNN YSIDE BLVDSR 52927TH AVE NECEDAR AVE4TH ST47TH AVE NE100TH ST NE51ST AVE NEMARINE DR152ND ST NE 83RD AVE NEGROVE ST 64TH ST NE 172ND ST NE STATE AVE67TH AVE NESR 9I-5 E L AKE GOODWIN RDLAKEWO O D RD SR 53 1140TH ST NE M A RIN E DR City of Arlington City of Marysville City of Lake Stevens Tulalip Reservation SEWERBASINS City of Everett Tulalip Indian Reservation PLANNING AREA #2 PLANNING AREA #3 PLANNING AREA #5 PLANNINGAREA #1 PLANNING AREA #4 Sewer service area (UGA) Marysville City Limits Other City Limits Planning Area #1 Planning Area #2 Planning Area #3 Planning Area #4 Planning Area #5 Sewer Basins Sewer Comprehensive Plan Sewer Basin Area & Planning Areas 0 1 20.5 Miles Figure E-1 E-2 City of Marysville November 2011 Sewer Comprehensive Plan TABLE E-1 Projected Sewer Service Population Summary ! ! ! *Service Area includes West Marysville and Arlington Interlocal Agreement EXISTING FACILITIES Chapter 5 provides a description of City’s wastewater collection system, pump stations, wastewater treatment plant and disposal facilities. The gravity collection system includes 210 miles of pipeline with diameters 6-inch to 48-inch. Approximately 60 percent of the pipelines are 8-inch diameter and approximately two-thirds (67%) of the collection system is constructed with PVC pipe material. In addition to the gravity pipe system, the City operates and maintains 15 pump stations, approximately 4.2 miles of force main pipe and 3.9 miles of effluent discharge piping to the City of Everett’s deep water outfall. The City’s primary pump stations are Soper Hill, Sunnyside, 51st Avenue, 88th Street, Marysville West, and West Trunk. The other 9 pump stations are smaller developer-type stations. A major upgrade to the City’s wastewater treatment plant was completed in 2004. Improvements included the addition of four complete-mixed aerated lagoon cells, hydraulic curtains, effluent filter expansion, UV disinfection facilities, effluent pump upsizing, and a new pipeline to Everett for seasonal disposal of treated effluent in Port Gardner Bay. This upgrade increased the plant capacity from 6.1 mgd (maximum month design) to 12.7 mgd. In addition, the plant loading capacity, as measured by BOD5 increased from 10,200 lbs/day to 20,143 lbs/day. Essentially, the upgrade doubled the wastewater treatment plant capacity. WASTEWATER CHARACTERISTICS AND FLOWS Chapter 6 quantifies the wastewater from the City’s service area estimated from treatment plant flow records and domestic water system records from the City. Use of the City’s water records for wintertime consumption, established a sewer base flow of 182 gallons per day for a single-family residence, or ERU. For the total sewer system, the estimated base flow is 4.45 mgd. Recorded wastewater flow above this value is attributed to infiltration and inflow (I/I). Infiltration and inflow for the City’s system is not excessive, yet represents approximately 6 percent of the average annual flow. During particularly wet periods, or maximum month conditions, I/I increases to approximately 27 percent of the total flow. City of Marysville E-3 Sewer Comprehensive Plan November 2011 Table E-2 presents both current and projected wastewater flows and loadings for the City’s Wastewater Treatment Plant (WWTP). TABLE E-2 Current and Projected Flows and Loadings Year 2011 2017 2031 ERUs 24,427 30,084 42,413 Flows (gpd) Sewer Service Area (ac.) 4,979 5,708 7,340 Total Baseflow 4,030,000 5,480,000 7,720,000 Dry Season Average Flow 4,160,000 5,240,000 7,620,000 Average Annual Flow 4,730,000 5,830,000 8,230,000 Maximum Month 6,120,000 7,600,000 11,250,000 Peak Day 9,310,000 10,530,000 13,790,000 Peak Hour(1) 10,700,000 12,710,000 16,880,000 Peak Hour Factor 2.26 2.18 2.05 Loading (lb/day) Annual Average BOD5 10,419 12,846 18,110 Maximum Month BOD5 13,812 16,997 23,963 Annual Average TSS 10,029 12,365 17,432 Maximum Month TSS 14,356 17,689 24,939 (1) Peak Hour Flow: Average Annual Flow x Peaking Hour Factor COLLECTION SYSTEM EVALUATION Chapter 7 develops the hydraulic model of the City’s service area used as a tool to assess the capacity and deficiencies of the existing collection system and pump stations. The hydraulic model, InfoSewer developed by Innovyze (formerly MWHSoft), was used to analyze the major gravity lines within the collection system for 2011, 2017, 2031. Inputs for the hydraulic model include invert elevations for manholes and pipeline lengths and unit residential and commercial flows developed in Chapter 6. Infiltration and inflow were developed from existing plant records and water consumption records. The hydraulic model was run for 2011, 2017, and 2031 conditions as shown in Table E-2. The model results indicated a total of 118 pipeline deficiencies thru 2031. A number of these deficiencies were determined to be insignificant enough to warrant a 6-year capital improvement based on modeling alone. These areas were analyzed separately and have been added to the City’s ongoing inspection list. Other pipe segments either deemed critical by the City or would be subject to future development were identified as a capital improvement. E-4 City of Marysville November 2011 Sewer Comprehensive Plan The most serious current deficiencies with the collection are low velocity pipelines (<2.0 fps). Of the 318,865 lf of pipeline modeled, approximately 50 percent were found to have low velocities. Most of these pipelines are large enough to provide adequate capacity, but these low velocity pipelines will collect grease and inert material and require more frequent cleaning and flushing. City staff recognizes this problem and have a maintenance program in place to clean its gravity sewers every two years. In addition, the City has a wastewater pretreatment program to limit grease discharged to its collection system. The hydraulic model results for 2031 show nearly double the number of capacity deficiencies than the 2011 and 2017 results, mostly due to the assumptions set forth in Chapter 3 to project future sewer service area population. One area of the collection system with a large number of future deficiencies is the Smokey Point area near I-5. The recommended approach to address deficiencies in this area is to divert flow to future pipelines to the Lakewood Sewer Extension rather than pipeline replacement in this commercial area. The other areas with a few surcharged pipelines in 2031 are located in East Sunnyside and Getchell Hill areas. Where these pipelines were not already part of the City’s CIP, they have been added to the 20-year CIP Plan. Most of the City’s pump stations have adequate capacity through 2031. The West Trunk Pump Station will be near its capacity prior to 2017 and improvements are included in the 6 year CIP. The 51st Street and Soper Hill pump stations will near their capacity prior to 2031 as well. They are both included for improvements in the 20 year CIP. Buildout conditions were also modeled using an estimated buildout population of approximately 160,000. The primary, long-term impacts to the City’s collection system are the upper reaches of Trunk A from 103rd Street to 143rd Street. In addition, several pipeline areas for Trunk D and CE are undersized for buildout conditions. In general, the hydraulic model is only one tool for assessing the condition of the collection system. Where “sagging” has occurred, offset joints have developed or manholes have been improperly installed, the hydraulic model most likely will not reflect those problems. Where the model has identified capacity deficiencies, particularly for 2031 and buildout, it is recommended that the model results be confirmed by survey, TV inspection, or a flow study prior to the capital expense of pipeline replacement. WASTEWATER TREATMENT EVALUATION Chapters 8 and 9 evaluate the City’s WWTP. The projected peak hour flow for 2031 of 16.9 mgd as presented in Table E-2 is less than the WWTP’s hydraulic design capacity of 20.3 mgd following the 2004 plant upgrades. Thus, the WWTP has sufficient hydraulic capacity for the next 20 years. City of Marysville E-5 Sewer Comprehensive Plan November 2011 The projected loadings, however, for 2031 exceed the plant’s design capacity for both BOD5 and TSS. The City had plans for two additional complete-mix aerated cells, to be constructed by 2015 to ensure adequate treatment capacity, but due to lower than projected flows and loadings, the construction of those can be moved further out into the future. Other future improvements include repairs to the influent parshall flume, installation of mechanical barscreens with smaller spacing between bars or an alternative screening method, upsizing of the filter reject pump station, extension of the filter reject line from the west trunk pump station to complete mix cell 1A, and construction of a pre- settling basin to be used prior to effluent filtration. The most significant item for the City’s WWTP operation is biosolids removal. The City last removed biosolids from its lagoon system in 2003. Biosolids removal was evaluated in 2011 and it was determined that the removal could wait until 2018 or beyond due to lower than expected accumulations. A biosolids profile is projected to be completed in 2016 to assess sludge depth, location, and quantities. Each biosolids removal project is expected to cost in excess of $3.0 million. OPERATION AND MAINTENANCE Chapter 10 addresses the operation and maintenance staff for the City’s wastewater treatment plant and collection system. Currently, there are approximately 15 full-time employees both for the WWTP and collection system. Of this number, four are assigned to the wastewater treatment plant operations and four are assigned to wastewater treatment plant and pump station maintenance. The remaining employees are assigned to the flushing, cleaning, inspection and repair of the collection system. For future operation and maintenance needs, City staff is adequate for its WWTP. However, the collection system will continue to expand with population growth and the City will need to add to staff in order to maintain the gravity sewers, force mains, and pump stations. One additional employee should be added to staff in 2017, with another added in 2031. CAPITAL IMPROVEMENT PLAN Chapter 11 summarizes the CIP and prioritizes projects identified in this Plan. Summaries of each capital improvement project include proposed construction dates, and estimated project costs (including construction, contingency, administration, sales tax, and engineering). Table E-3 and Figure E-2 present the 6-year CIP projects. CIP Projects up to 2031 are shown in Chapter 11. Future projects that are not identified as part of the City’s CIP may become necessary. Such projects may be required in order to remedy an emergency situation, to address unforeseen problems, or to accommodate improvements from adjacent jurisdictions. Due to budgetary constraints, the completion of such projects may require modifications to the recommended CIP. The City retains the flexibility to reschedule, expand, or reduce the E-6 City of Marysville November 2011 Sewer Comprehensive Plan projects included in the CIP and to add new projects to the CIP, as best determined by the Council, when new information becomes available for review and analysis. The total 6-year CIP is $10,207,000. Amounts for each of the four categories for the 6- year CIP are shown below: Sanitary Sewer Mains ................................................................ $ 4,630,000 Pump Stations ............................................................................ $ 1,575,000 WWTP Improvements ............................................................... $ 3,402,000 General System Improvements .................................................. $ 600,000 Total: 6-Year CIP ................................................................... $10,207,000 SS-D 71st St NE Sewer Upsizing 64th Ave NE to 66th Ave NE SS-C Whiskey Ridge Sewer Extension Gravity Main SS-E Trunk G Rehab Cedar to Columbia PS-B West Trunk Pump Station Upsizing PS-A Whiskey Ridge Sewer Pump Station & Force Main PS-C Carroll's Creek Pump StationEmergency Generator Installation PS-D Cedarcrest Vista Pump StationEmergency Generator InstallationI-5SR 967TH AVE NESTATE AVESR 9251ST AVE NESR 529GROVE ST 83RD AVE NE27TH AVE NE64TH ST NE 84TH ST NE 108TH ST NESMOKEY POINT BLVD152ND ST NE MARINE DR140TH ST NE SUNNYSIDE BLVD99TH AV NE47TH AVE NE4TH ST 100TH ST NE 88TH ST NE CEDAR AVE116TH ST NE 8TH ST FORTY-FIVE RD 172ND ST NE BEACH AVE136TH ST NE 44TH ST NE 132ND ST NE 71ST AVE NE3RD AVE NE80TH ST NE ASH AVE34TH AVE NE48TH DR NE140TH ST NW FORTY FIVE RD 40TH ST NESHOULTES RD1ST ST 76TH ST NE M AR IN E D R N E 52ND ST NE 99TH AV NEI-534TH AVE NE172ND ST NE 51ST AVE NE88TH ST NE 51ST AVE NE84TH ST NE 132ND ST NE 2011 Six Year CIP Pump Stations 2011 Six Year CIP Lines71st St NE Sewer Upsizing 64th Ave NE to 66th Ave NE Trunk G Rehab Cedar to Columbia Whiskey Ridge Sewer Extension Force Main Whiskey Ridge Sewer Extension Gravity Main Urban growth area 0 2,000 4,000 6,0001,000 Feet Sewer Comprehensive Plan Figure E-2 Six Year CIP E-7 City of Marysville November 2011 Sewer Comprehensive Plan TABLE E-3 6-Year Capital Improvements Plan(1) 2011 2012 2013 2014 2015 2016 2017 Sanitary Sewer Mains a. Sewer Main Oversizing $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 b. Renewals and Replacement $0 $300,000 $300,000 $300,000 $300,000 $300,000 c. Whiskey Ridge Sewer Extension $200,000 $1,200,000 d. 71st St NE Sewer Upsizing: 64th Ave NE to 66th Ave NE $410,000 e. Trunk “G” Rehab.: Cedar to Columbia $1,340,000 Total Sanitary Sewer Mains $230,000 $1,230,000 $330,000 $330,000 $740,000 $1,670,000 $330,000 Pump Stations a. Whiskey Ridge Sewer Lift Station and Force Main $1,000,000 b. West Trunk Pump Station Upsizing $225,000 c. Carroll’s Creek Pump Station Emergency Generator Installation $175,000 d. Cedarcrest Vista Pump Station Emergency Generator Installation $175,000 Total Pump Station Improvements $0 $0 $225,000 $1,000,000 $0 $175,000 $175,000 E-8 City of Marysville November 2011 Sewer Comprehensive Plan TABLE E-3 - (continued) 6-Year Capital Improvements Plan(1) 2011 2012 2013 2014 2015 2016 2017 WWTP Improvements a. Biosolids Removal $300,000 $300,000 $300,000 $300,000 b. Replacement/Reconstruction of Headworks Parshall Flume $50,000 c. Filter Reject Line Extension $100,000 d. Upsize Filter Reject Wet Well and Pump System $500,000 e. Pre-Settling Basin $1,000,000 f. Screen Replacement for Mechanical Screens $500,000 g. Flow Study 40,000 h. Preliminary Biosolids Profile $12,000 i. Wastewater Treatment Plant Generator $400,000 Total WWTP Improvements $400,000 $0 $190,000 $800,000 $1,300,000 $312,000 $800,000 General System Improvements Cost of Service Study $250,000 Sanitary Comp. Plan/Model $300,000 $300,000 Sewer Rate Study $50,000 Total General Sewer Improvements $300,000 $0 $50,000 $0 $0 $250,000 $300,000 Total Sanitary Sewer $930,000 $1,230,000 $795,000 $2,130,000 $2,040,000 $2,407,000 $1,605,000 (1) The 6-year CIP covers the period of 2012 - 2017. 2011 CIP projects are included for reference. City of Marysville 1-1 Sewer Comprehensive Plan November 2011 CHAPTER 1 INTRODUCTION This Sewer Comprehensive Plan (Plan) for the City of Marysville addresses comprehensive planning needs for wastewater collection, transmission, treatment, and disposal for the next twenty years. This Plan has been prepared in accordance with the provisions of the Revised Code of Washington (RCW), Section 90.48, Water Pollution Control; Washington Administrative Code (WAC) Section 173-240-050, General Sewer Plan; and WAC 173-240-060, Engineering Report. Development of the Plan has been coordinated with the 2005 City of Marysville Comprehensive Plan, Snohomish County 2006 Comprehensive Plan, the City of Marysville 2005 Comprehensive Sanitary Sewerage Plan, and with the City of Marysville 2009 Water System Plan Update. WASTEWATER SYSTEM OWNERSHIP AND MANAGEMENT The City of Marysville owns and operates a sanitary sewer system and wastewater treatment facility. The Mayor and seven council members oversee and provide review and approval authority for issues that relate to the City’s public works systems. The Department of Public Works maintains and operates the sewer, water, drainage, solid waste, and street systems, including construction, engineering, construction inspection, and fleet and facilities. The Director of Public Works oversees two departments managed by the Assistant City Engineer and Public Works Superintendent. The Public Works Director directly manages the City’s facilities division. The City’s addresses and telephone numbers are listed below and a location map is shown in Figure 1-1. City of Marysville City Hall City of Marysville Public Works 1049 State Avenue 80 Columbia Avenue Marysville, Washington 98270 Marysville, Washington 98270 (360) 363-8000 (360) 363-8100 PURPOSE The purpose of this Plan is to address the City’s comprehensive planning needs for wastewater collection, transmission, treatment, and disposal for the next 20 years. In 2004 the City completed significant improvements to its wastewater treatment plant (WWTP) and effluent disposal system. These improvements included modifications to its aerated lagoons, installation of UV disinfection, and construction of an effluent pump station and pipeline intertie with the City of Everett for effluent disposal in Puget Sound. These improvements were designed for WWTP compliance with the City’s NPDES permit, No. WA-002249-7, and for an increase in plant capacity. A copy of the NPDES permit is included as Appendix A. 1-2 City of Marysville November 2011 Sewer Comprehensive Plan The primary focus of this Plan is to continue development of the hydraulic model of the City’s sanitary sewer system consistent with GIS, provide preliminary plans to provide sewer service to new areas, and to develop a capital improvement plan with cost estimates and schedule for six- and twenty-year planning periods. The City of Marysville has experienced rapid growth over the past twenty years that has required an expansion of its sanitary sewer system. In 1980, the City’s population was 5,000; by 1992 the population increased to 14,122 and to 60,183 in 2010 (inclusive of the urban growth area (UGA)). Future population projections show the UGA exceeding 84,989 by 2031. This Plan addresses known wastewater system planning issues, assesses the condition and capabilities of the existing sewer system and wastewater treatment plant, develops a plan for the level of service within the defined study area, and determines the required system improvements including project construction schedules and costs. SCOPE The City of Marysville Sewer Comprehensive Plan is organized into twelve chapters as follows: Chapter 1, Introduction, includes descriptions of the purpose and scope of the Plan and provides background information used to address the issues discussed in this Plan. Chapter 2, Sewer Service Area, includes a description of study area boundaries and physical environment. Chapter 3, Land Use and Planning Criteria, reviews general planning issues, including growth management, land use, and zoning, and provides current and projected population. Chapter 4, Regulatory Requirements, consists of descriptions of pertinent regulations that apply to the City’s wastewater collection, treatment and effluent disposal facilities. Chapter 5, Existing Facilities, describes and assesses the existing components of the collection system, wastewater treatment plant, and sewer agreements with adjacent jurisdictions. Chapter 6, Wastewater Flows and Loading, applies planning information and historical records to establish design criteria for existing and future flows and loadings. Chapter 7, Collection System Evaluation, presents a computer model of the sewer system components, including pump stations, force mains, and gravity lines 16THAVE NW132ND ST NE 99TH AVE NESR 52834TH AVE NE79TH AVE NE71ST AVE NESR 92 76TH ST NE 84TH ST NE SR 980TH ST NE ASH AVE116TH ST NE SR 984TH ST NE 52NDST NESHOULTES RD132ND ST NE 108TH ST NE SR 531 67TH AVE NE SMOKEY POINT BLVDI-5 I-551ST AVE NE88TH ST NE 67TH AVE NE 51ST AVE NE I-523RDAVE NEARMARRD140TH ST NE 48TH DR NE136TH ST NE FORTY-FIVE RD3RD AVE NE44TH ST NESUNN YSIDE BLVDSR 52927TH AVE NECEDAR AVE4TH ST47TH AVE NE100TH ST NE51ST AVE NEMARINE DR152ND ST NE 83RD AVE NEGROVE ST 64TH ST NE 172ND ST NE STATE AVE67TH AVE NESR 9I-5 E L AKE GOODWIN RDLAKEWO O D RD SR 53 1140TH ST NE M A RINE D R City of Arlington City of Marysville Tulalip Reservation City of Everett City of Lake Stevens Snohomish County Snohomish County SewerComprehensivePlan Fig 1-1 Location Map 0 1 20.5 Miles Sewer service area Future planning areas Marysville city limits Other city limits City of Marysville 1-3 Sewer Comprehensive Plan November 2011 and provides modeling results at current and future flows to identify deficiencies and improvements. Chapter 8, Wastewater Treatment Plant Analysis, evaluates plant capacity and effluent discharge based on projected flows and loadings. Chapter 9, Biosolids Management, evaluates the existing methods of biosolids disposal and estimates the schedule for future biosolids removal projects. Chapter 10, Operation and Maintenance, provides an overview of the City’s operation and maintenance program including a summary of existing and future staffing needs. Chapter 11, Capital Improvement Plan, recommends sewer system and wastewater treatment plant improvements and provides cost estimates and an implementation schedule for those improvements. Chapter 12, Financial Program, provides an assessment of current financial status of the utility, discusses available and potential revenue sources for system improvements, assesses the General Facilities Charge, and establishes operation and maintenance costs that relate to the recommended Capital Improvement Plan (CIP). HISTORY OF WASTEWATER SYSTEM DEVELOPMENT The development of the City’s wastewater facilities parallels the growth of its population and land area. The City of Marysville was established as a Fourth Class City in 1891, with a population of 350 residents. Its early development depended on the abundant timber resources and the construction of the Great Northern Railroad. The construction of Highway 99 between Everett and Marysville provided an additional development boost to the City. In 1905, the City’s population was 1,250 and it was not until 1954 that the population doubled to 2,500. The earliest sewers to serve the Marysville downtown core were constructed prior to 1940. The first sanitary sewers were combined sewers collecting both wastewater and stormwater. The downtown combined sewers were eventually separated through a series of capital improvement projects. An extensive expansion of the original sewer system was completed over the past 35 years. As reported in the 1997 Comprehensive Sanitary Sewerage Plan (Hammond, Collier & Wade-Livingstone Associates), trunk sewers C, D, and G extended the sewer system north, east, and west in 1968. In 1970, trunk sewer A was constructed to serve the area northeast of Marysville. 1-4 City of Marysville November 2011 Sewer Comprehensive Plan In 1982, the City established boundaries for its Rural Utility Service Area (RUSA) as a basis for planning for water and sewer service. The RUSA covered approximately 12 square miles. By 1991, the sanitary sewer system had 6,755 connections with 6,233 residential customers and 522 school, commercial, and institutional customers. Chapter 14.32, Utility Service Area, of the Marysville Municipal Code (MMC) replaced the RUSA with the Utility Service Area (USA). The USA set the boundaries of the sanitary sewers service area. In 1990, a Sewer Comprehensive Plan was prepared by Hammond, Collier & Wade- Livingstone that set the groundwork for a major upgrade to the City’s wastewater treatment plant in 1994. The recommended improvements subsequently included a major modification of the 72-acre lagoon system. The project included development of two 2.5 acre complete mix aerated lagoon cells, installation of two 10,600 gpm recirculation pumps to increase lagoon treatment capacity, a new headworks facility with a mechanical bar screen, and two 4,500 gpm influent screw lift pumps. The improvements also included new deep bed single media sand filters to treat up to 2,400 gpm of plant effluent, a new chlorine contact chamber with chlorination facilities, and a 3,000 gpm lift station upstream of the plant. The 1994 improvements increased plant capacity from 2.8 mgd to 6.1 mgd. In addition, a new 28-inch HDPE outfall pipe and pump station were installed to convey effluent to Steamboat Slough. The 1997 Sewer Comprehensive Plan prepared by Hammond, Collier & Wade- Livingstone and KCM set the ground work for the 2004 upgrades to the City’s wastewater treatment plant. Phase 1 of the upgrades included 2 additional completed mix cells, one additional influent screw pump, one additional barscreen, and upsizing of the effluent pumps. Phase 2 added 1600 SF to the effluent sand filters, a new maintenance facility, UV disinfection, and an effluent pipeline to the City of Everett’s South Everett Pump Station in route to the Deep Marine Outfall in Puget Sound (Port Gardner Bay). The 2004 upgrades to the City’s wastewater treatment plant increased plant capacity from 6.1 MGD to 12.7 MGD. In 1990, the State of Washington enacted the Growth Management Act (GMA). The GMA developed criteria for urban growth areas, which superceded the need for the Rural Utility Service Area (RUSA). In 1996, the City’s Planning Department completed its first Comprehensive Plan under GMA. By 1996, the estimated number of sewer connections was 8,957, a 40 percent increase over the number of connections in 1991. Table 1-1 provides a history of sewer connections since 1990. Since 1990, the City has experienced rapid growth in residential connections, but a declining number of non- residential customers since 1998. City of Marysville 1-5 Sewer Comprehensive Plan November 2011 During the past 10 years, the City has added an average of 464 connections per year to its sewer system. TABLE 1-1 City of Marysville Sewer Service Connections Growth Year Residential Customers Non- Residential Customers New Customers Total 1990 6,130 296 -- 6,426 1991 6,439 344 357 6,783 1992 6,763 399 379 7,162 1993 7,104 463 405 7,567 1994 7,462 537 432 7,999 1995 8,013 624 638 8,637 1996 8,393 724 480 9,117 1997 9,014 818 715 9,832 1998 9,496 778 442 10,274 1999 10,004 712 442 10,716 2000 10,540 620 444 11,160 2001 11,003 600 443 11,603 2002 11,604 620 621 12,224 2003 12,330 691 797 13,021 2004 12,831 703 513 13,534 2005 13,327 703 496 14,030 2006 13,774 717 461 14,491 2007 14,202 723 434 14,925 2008 14,474 724 273* 15,198 2009 14,700 730 232* 15,430 2010 15,064 734 368* 15,798 Data on connections for the years 1990 through 1996 were obtained from the City of Marysville 1997 Comprehensive Sanitary Sewerage Plan. Data after 1996 from City of Marysville sources. * New customers totals are based on connection fees paid. Connection fees were prepaid at final plat. However, based on economic conditions during this time, many plats remain empty and parcels are not actually connected to the sewer. Therefore, the total number of residential customers is not equal to the total number of customers actually being billed. 1-6 City of Marysville November 2011 Sewer Comprehensive Plan PROJECTS COMPLETED SINCE THE 2005 COMPREHENSIVE SANITARY SEWERAGE PLAN The Sewer Comprehensive Plan was last updated in April 2005. Table 1-2 provides the projects listed in the Capital Improvement Plan (CIP) included in the 2005 Plan and the status of each project for both the collection system and the wastewater treatment plant. TABLE 1-2 Projects Completed Since 2005 Sanitary Sewerage Plan CIP Project Description Status or Year Completed Sanitary Sewer Mains Sewer Main Oversizing Ongoing Smokey Pt. Blvd Ext. 116th – 136th 2006 Smokey Pt. Blvd. Ext. 136th – 152nd 2009 State Avenue Trunk 98th – 113th LID 2003 Trunk “G” Rehab. Beach – 1st 2006 (west of BNRR only) Lakewood Sewer Extension: Phase 1 2006 Lakewood Sewer Extension: Phase 2 2009* Renewals and Replacement Ongoing Soper Hill Road Ext. 71st – 83rd 2004 88th Street at 60th Drive 2006 70th Drive and 88th (Trunk C) 2006 Delta Avenue 5th – 9th 2007 State Avenue 1st – Grove 2004 Pump Stations Regan Road Pump Station 2005 General Sewer Improvements Cost of Service Study 2008 Sanitary Comp. Plan/Model In Progress Sewer Rate Study 2007 Wastewater Treatment Plant Improvements Phase II WWTP 2004 MV/Everett Effl. Horizontal Drilling 2004 MV/Everett Effl. Open Cut 2004 So. Everett Pumping Station 2004 Cross Town 2004 Everett (Deep Water) 2004 Extra Capacity 2005 Flow Study 2005 *Partially constructed along Smokey Point Blvd from 136th St NE to 148th St NE. City of Marysville 1-7 Sewer Comprehensive Plan November 2011 RELATED PLANNING DOCUMENTS The following documents were consulted in the preparation of the City of Marysville System Comprehensive Plan. WATER SYSTEM PLANS City of Marysville 2009 Water System Plan Update, HDR Engineering, Inc. June 2009. The Water System Plan evaluated the existing water system to identify existing and future demands, review and recommend capital project to address the needs of the system, and ensure that the system has the operational, technical, staff, and financial ability to comply with all local, state, and federal regulations, including local planning efforts. The recommended capital improvements through the year 2014 were estimated to cost $37,578,000, with an additional $40,470,000 to the year 2028. Relevant information includes land use, population, equivalent residential units, and water demands. WASTEWATER COMPREHENSIVE/FACILITY PLANS City of Marysville Wastewater Treatment Plant Capital Facilities Plan, Tetra Tech/KCM, Inc., February 2001 The Wastewater Treatment Plant Capital Facilities Plan reviewed the hydraulic capacity of the treatment process and recommended improvements to provide adequate capacity to the year 2020. Alternatives were reviewed for the upgrade of the wastewater treatment plant that included cost estimates and schedule for implementation. The plan estimated the cost of the recommended improvements in the amount of $69,320,000. City of Marysville Comprehensive Sanitary Sewerage Plan, Gray and Osborne, Inc., April 2005 The purpose of this Comprehensive Sanitary Sewerage Plan was to prepare a long-range plan to develop an adequate sanitary sewer system to the year 2031. The Plan updates land use and population data, incorporates recent changes to the sewer service area, evaluates the system for infiltration and inflow, integrates a computerized hydraulic model to assess capacity of the existing collection system and provides a capital improvement plan for the City and its urban growth area. 1-8 City of Marysville November 2011 Sewer Comprehensive Plan GMA COMPREHENSIVE PLANS City of Marysville Comprehensive Plan, April 2005 Snohomish County Comprehensive Plan, General Policy Plan, February 2006, amended as of January 2011 City of Marysville 2-1 Sewer Comprehensive Plan November 2011 CHAPTER 2 PLANNING AREA INTRODUCTION The configuration of a sewer system can be influenced by many factors including development trends, political considerations, and topography. Sewer lines should follow natural drainage patterns to maximize gravity flow. A comprehensive sewer plan establishes a sewer service area based on topography, the drainage characteristics of the area, and the City’s growth objectives. Modifications may then be made in consideration of the influence of existing facilities, political boundaries, and growth patterns before finalizing a specific plan. The Marysville planning area consists of three components; the City’s corporate boundary, the existing Urban Growth Area (UGA), and the ultimate planning boundary. PLANNING AREA The City of Marysville is located in Snohomish County approximately 5 miles north of the City of Everett. The City is surrounded by the communities of Everett to the south, Lake Stevens to the southeast, Arlington to the north, and the Tulalip Indian Reservation to the west. Other areas are adjacent to rural Snohomish County. The location of the City in relation to surrounding jurisdictions is presented in Figure 2-1. The City of Marysville planning area includes the City of Marysville (City), the Marysville Urban Growth Area (UGA), and the Marysville Ultimate Planning Boundary as shown in Figure 2-2. The Ultimate Planning Boundary includes areas that are outside of the City UGA but have the potential for future development and sewer service and inclusion into the UGA. Long range planning for these planning areas is covered by an interlocal agreement between the City and Snohomish County and included in Appendix B. The current City planning area encompasses a total area of approximately 24,000 acres (37.5 square miles) as indicated in Table 2-1. TABLE 2-1 Planning Area Acreage Location Acreage City of Marysville (City) 13,370 Marysville (UGA) 13,660 Ultimate Planning Boundary 24,000 16THAVE NW132ND ST NE 99TH AVE NESR 52834TH AVE NE79TH AVE NE71ST AVE NESR 92 76TH ST NE 84TH ST NE SR 980TH ST NE ASH AVE116TH ST NE SR 984TH ST NE 52NDST NESHOULTES RD132ND ST NE 108TH ST NE SR 531 67TH AVE NE SMOKEY POINT BLVDI-5 I-551ST AVE NE88TH ST NE 67TH AVE NE 51ST AVE NE I -523RDAVE NEARMARRD140TH ST NE 48TH DR NE136TH ST NE FORTY-FIVE RD3RD AVE NE44TH ST NESUNN YSIDE BLVDSR 52927TH AVE NECEDAR AVE4TH ST47TH AVE NE100TH ST NE51ST AVE NEMARINE DR152ND ST NE 83RD AVE NEGROVE ST 64TH ST NE 172ND ST NE STATE AVE67TH AVE NESR 9I-5 W LAKE GOODWIN RDE L AKE GOODWIN RDLAKEWO O D RD SR 53 1140TH ST NE MARINE DR MARIN E DRCity of Arlington City of Marysville Tulalip Reservation City of Everett City of Lake Stevens SewerComprehensivePlan Fig 2-1 Adjacent Jurisdictions 0 1 20.5 Miles Cty Limits Urban Growth Areas Lake Stevens Sewer District Tulalip Reservation 16THAVE NW132ND ST NE 99TH AVE NESR 52834TH AVE NE79TH AVE NE71ST AVE NESR 92 76TH ST NE 84TH ST NE SR 980TH ST NE ASH AVE116TH ST NE SR 984TH ST NE 52NDST NESHOULTES RD132ND ST NE 108TH ST NE SR 531 67TH AVE NE SMOKEY POINT BLVDI-5 I-551ST AVE NE88TH ST NE 67TH AVE NE 51ST AVE NE I-523RDAVE NEARMARRD140TH ST NE 48TH DR NE136TH ST NE FORTY-FIVE RD3RD AVE NE44TH ST NESUNN YSIDE BLVDSR 52927TH AVE NECEDAR AVE4TH ST47TH AVE NE100TH ST NE51ST AVE NEMARINE DR152ND ST NE 83RD AVE NEGROVE ST 64TH ST NE 172ND ST NE STATE AVE67TH AVE NESR 9I-5 E L A KE GOODWIN RDLAKEWOO D RD SR 53 1140TH ST NE MARINE DR City of Arlington City of Marysville Tulalip Reservation City of Everett City of Lake Stevens Getchell Smokey Point Downtown Marshall Pinewood Kellogg Marsh Lakewood Sunnyside Shoultes Jennings Park East Sunnyside PLANNING AREA #2 PLANNING AREA #3 PLANNING AREA #1 PLANNING AREA #6 PLANNING AREA #4 PLANNING AREA #5 SewerComprehensivePlan Fig 2-2 Corporate Boundaries and Planning Areas 0 1 20.5 Miles Urban Growth Area Future Planning Areas Neighborhoods Marysville city limits Other city limits 2-2 City of Marysville November 2011 Sewer Comprehensive Plan NATURAL FEATURES OF THE PLANNING AREA Various natural features of the planning area are discussed below, including climate and precipitation, geography, topography, soils and geology, surface water, and site sensitive areas. Information on the public utilities available in the area is also presented. TOPOGRAPHY AND GEOGRAPHY The topography of the City of Marysville has a significant influence on the sewer system. The City is in an area known as the Marysville Trough. The trough is a long flat valley gently sloping to the south and bordered to the west by the Tulalip Plateau and to the east by the Getchell Hill Plateau. The northern and eastern portions of the City slopes southwest towards Ebey Slough. The elevations of the Trough vary from sea level at the slough to more than 90 feet above sea level at the north end. The elevations to the east rise sharply to elevations up to 430 feet. The contours of the planning area and surrounding region are shown in Figure 2-3. SOILS AND GEOLOGY The classification of soils within the City of Marysville is provided by the 1983 Soils Survey for Snohomish County Area, compiled by the Natural Resource Conversation Service (formerly known as the Soil Conservation Service). A soils map is presented in Figure 2-4. The major classifications of soils within the Trough area are Ragnar, Norma, and Custer. Ragnar is a very deep well drained soil located on outwash plains. The surface layer is dark brown fine sandy loam about 2 inches thick. The subsoil is dark brown and brown sandy loam about 22 inches thick. The substratum to a depth of 60 inches or more is dark yellowish brown and dark gray loamy sand and sand. In some areas the surface layer is loamy, the subsoil is gravelly, and the substratum is very gravelly. Permeability of the soil is moderately rapid and water runoff is slow. According to the Natural Resource Conversation Service, if the density of housing is moderate to high, community sewage systems may be needed to prevent contamination of water supplies as a result of seepage from onsite sewage disposal systems. Norma is very deep, poorly drained soil located in depressional areas on outwash plains and till plains. The surface layer is dark gray loam about 10 inches thick. The subsoil is dark grayish brown sandy loam about 18 inches thick. The substratum to a depth of 60 inches or more is dark gray sandy loam. Permeability of the soil is moderately rapid and available water capacity is moderate. The soil is limited by a high water table and underlying till, therefore, runoff is very slow. The soil is classified as poorly suited to urban development and subject to ponding of water. 50 100 100 50 50 500 450 400 350 350 400 350300250 100150 200250 300 400 450 500 550 600 150 200 250300350 400450 500 100 50 450 550 550 500 City of Arlington City of Marysville City of Lake Stevens City of Everett I-5 SR 967TH AVE NESR 92STATE AVEHWY 530 SR 52951ST AVE NEJ O R D A N R D 84TH ST NE M A RIN E D R 83RD AVE NE27TH AVE NE64TH ST NE3RD AVE NE108TH ST NE 140TH ST NW 152ND ST NE 140TH ST NE 99TH AV NE100TH ST NE 88TH ST NE FORTY-FIVE RD 172ND ST NE 136TH ST NE 44TH ST NE 132ND ST NE 79TH AVE NEW MARINE VIEW DRWILLOW DRI-599TH AV NE172ND ST NE Sewer Comprehensive PlanFigure 2-3 Area Topography Sewer service area (UGA) City limits Future planning areas 50' contours 0 1 20.5 Miles Elevation 615'0' 4 22 18 4 12 91 18 12 4 9 1 10 9 22 22 4 4 8 3 20 13 12 18 22 1 12 12 17 25 22 4 12 9 18 1 17 11 3 8 2 6 26 5 24 27 15 25 21 13 23 20 I-5SR 967TH AVE NESTATE AVE51ST AVE NEG R O VE ST SR 529SR 9 283RD AVE NE27TH AVE NE64TH ST NE 108TH ST NE 84TH ST NE 152ND ST NE 140TH ST NE SUNNYSIDE BLVD99TH AV NE4TH ST 100TH ST NE 88TH ST NE MARINE DR116TH ST NE 8TH ST FORTY-FIVE RD 172ND ST NE 136TH ST NE 44TH ST NE 132ND ST NE 71ST AVE NE79TH AVE NE3RD AVE NE34TH AVE NE48TH DR NEI-599TH AV NE51ST AVE NE84TH ST NE 172ND ST NE Sewer Service Area (UGA) 1 - Alderwood gravelly sandy loam 2 - Alderwood-Everett gravelly sandy loams 3 - Bellingham silty clay loam 4 - Custer fine sandy loam 5 - Everett gravelly sandy loam 6 - Fluvaquents 7 - Indianola loamy sand 8 - Kitsap silt loam 9 - Lynnwood loamy sand 10 - McKenna gravelly silt loam 11 - Mukilteo muck 12 - Norma loam 13 - Norma variant loam 14 - Orcas peat 15 - Pastik silt loam 16 - Pits 17 - Puget silty clay loam 18 - Ragnar fine sandy loam 19 - Snohomish silt loam 20 - Sumas silt loam 21 - Terric Medisaprists 22 - Tokul gravelly loam 23 - Tokul silt loam 24 - Tokul-Winston gravelly loams 25 - Urban land 26 - Water 27 - Xerorthents 0 10.5 Miles Sewer Comprehensive PlanFigure 2-4 Area Soils City of Marysville 2-3 Sewer Comprehensive Plan November 2011 Custer is a very deep poorly drained soil located on outwash plains. The surface layer is very dark grayish brown fine sandy loam about 9 inches thick. The upper part of the subsoil is loamy fine sand about 7 inches thick. The lower part is gray and olive sand about 19 inches thick. The substratum is gray sand about 14 inches thick over gravelly coarse sand that extends to a depth of 60 inches or more. Permeability of the soil is slow in the hardpan and rapid below it. This soil also has a high water table with slow runoff and ponding occurs from November to March. The slopes above the Trough area on the east side of the City contain different soil types. The major classifications of these soils are Tokul and Bellingham. Tokul is a moderately deep, moderately well drained soil. The surface layer is dark brown gravelly loam about 4 inches thick. The subsoil is brown gravelly loam about 18 inches thick. The substratum is light brown gravelly fine sandy loam about 9 inches thick. A hardpan is located at a depth of about 31 inches. The permeability of this soil is moderate to the hardpan and very slow through it. Available water capacity is moderate and runoff is slow. The main limitations for septic tank absorption fields are the depth to the hardpan and wetness. Onsite sewage disposal systems often fail or do not function properly during periods of high rainfall. Bellingham is a very deep poorly drained soil. The surface layer is very dark gray silty clay loam about 9 inches thick. The subsoil to a depth of 60 inches or more is gray silty clay. Permeability of this soil is slow and the water capacity is high. Ponding can occur from November to June. The main limitations for septic tank absorption fields are slow permeability and ponding. Onsite waste disposal systems fail or do not function properly. SURFACE WATER The surface water in the planning area includes creeks, small ponds and sloughs. The large surface waters in the area are the marine sloughs to the south of the City including Ebey Slough, Steamboat Slough, and Union Slough. A slough is defined as a creek in a marsh or tide flat. Water in the sloughs comes from the Snohomish River and the lower reaches are influenced by tidal fluctuations. The outfall from the Wastewater Treatment Plant runs into Steamboat Slough, which flows into Possession Sound, a part of Puget Sound. The City of Marysville constructed a new effluent transfer pipeline, conveying effluent from the City of Marysville Wastewater Treatment Plant to the City of Everett Sewage Treatment Plant. The pipeline will enable the City of Marysville to divert effluent discharge during the summer months into the combined deep-water outfall in Port Gardner Bay, in order to meet summer water quality requirements for Steamboat Slough. During winter months, the water quality requirements for Steamboat Slough will be less stringent and the existing outfall can be used or flow could still be routed to Everett. 2-4 City of Marysville November 2011 Sewer Comprehensive Plan CLIMATE The climate of the Snohomish County area is tempered by winds from the Pacific Ocean. Summers are fairly warm with an occasional hot day. The closest and most reliable weather station is Everett, approximately five miles south of Marysville. The average summer temperature in Everett is 60 degrees Fahrenheit (F) with an average daily maximum temperature of approximately 72 degrees F. Winters are cool with occasional snow and freezing temperatures. The average winter temperature in Everett is 40 degrees F with an average daily minimum temperature of 34 degrees F. Summer rainfall is light, but rains during the rest of the year are frequent, particularly in the fall and winter. The average total annual precipitation for Everett is 36 inches. Approximately 20 to 30 percent of the total precipitation falls during the period of April through September. Average annual snowfall for the Everett area is 8 inches. Average wind speed is approximately 10 miles per hour and is highest in the winter. Usually one or two storms per winter bring damaging winds and heavy rains, which may result in power outages and flooding. SITE SENSITIVE AREAS Site sensitive areas within the planning area include those classified as wetlands, seismic hazard areas, slide hazard areas, flood hazard areas, and water bodies. The site sensitive areas within the planning area are described in the following sections. Erosion Hazard Areas These areas are especially subject to erosion, if disturbed, and may not be well suited for high-density developments or intensive land uses. Erosion hazard areas include areas with steep slopes, which are shown in Figure 2-5. Seismic Hazard Areas Seismic hazard areas are those with low-density soils that are more likely to experience greater damage due to seismic-induced subsidence, liquefaction, or landslides. The City of Marysville is located approximately 10 miles north of the Whidbey Island Fault. This fault runs from the Strait of Juan de Fuca along the southwestern edge of Whidbey Island, crosses Puget Sound, and continues through the Cities of Mukilteo, north Lynnwood, and south Mill Creek to Duvall. The Whidbey Island Fault has seen increased activity in the past 25 years including three earthquakes with a magnitude greater than 3.7 on the Richter Scale. The Geological Society of America Bulletin, March 1996 states “The southern Whidbey Island Fault should be considered capable of generating large earthquakes (Magnitude equal to or greater than 7) and may represent a significant seismic hazard to the Puget Lowland.” 16THAVE NW132ND ST NE 99TH AVE NESR 52834TH AVE NE79TH AVE NE71ST AVE NESR 92 76TH ST NE 84TH ST NE SR 980TH ST NE ASH AVE116TH ST NE SR 984TH ST NE 52NDST NESHOULTES RD132ND ST NE 108TH ST NE SR 531 67TH AVE NE SMOKEY POINT BLVDI-5 I-551ST AVE NE88TH ST NE 67TH AVE NE 51ST AVE NE I-523RDAVE NEARMARRD140TH ST NE 48TH DR NE136TH ST NE FORTY-FIVE RD3RD AVE NE44TH ST NESUNN YSIDE BLVDSR 52927TH AVE NECEDAR AVE4TH ST47TH AVE NE100TH ST NE51ST AVE NEMARINE DR152ND ST NE 83RD AVE NEGROVE ST 64TH ST NE 172ND ST NE STATE AVE67TH AVE NESR 9I-5 LAKEWO O D RD SR 53 1M ARINE D R Stream buffers Wetland buffers FEMA 100 Year Floodplain Top-of-bank 25' buffer Moderate landslide hazards Sewer service area (UGA) Future planning areas Sewer Comprehensive Plan Fig 2-5 Site Sensitive Areas 0 1 20.5 Miles City of Marysville 2-5 Sewer Comprehensive Plan November 2011 Flood Hazard Areas Flood hazard areas are those adjacent to lakes, rivers, and streams that are prone to flooding during peak runoff periods. Flood hazard areas deserve special attention due to the sensitive nature of their ecosystems as well as the potential for damage to structures located in the floodplain. The majority of the flood areas appear to be in the southwest corner of the City near Ebey Slough as shown in Figure 2-5. The flood plains in the area can also be seen on the Federal Emergency Management Agency (FEMA) flood maps panel numbers 535534 0190B and 535534 0180B. Slide Hazard Areas Slide hazards areas are those that are prone to unstable behavior due to steep slopes, lack of vegetation, or unconsolidated soils. The eastern portion of the planning area has the potential to slide due to the steep slopes as shown in Figure 2-5. Wetlands Wetlands are defined by the Environmental Protection Agency (EPA) as areas that are inundated for at least part of the year. Wetlands support valuable and complex ecosystems and consequently development is severely restricted if not prohibited in most wetlands. There are numerous wetlands in the planning area as shown in Figure 2-5. Water Bodies/major drainage basins Lakes and streams are classified as sensitive areas due to the variety of plants and animals that they support. The streams and creeks within the planning area are classified as having excellent water quality. The naturally occurring streams include the Quilceda Creek to the west and the Allen Creek to the east, both of which drain into Ebey Slough. The planning area is primarily located within two separate drainage basins as seen in Figure 2-6 and as described in the City’s Comprehensive Plan. The Quilceda drainage basin drains the Quilceda Creek and the Allen/Munson Creek drainage basin drains Allen Creek. The Quilceda drainage basin is the larger of the two with an area of approximately 38 square miles. The Allen/Munson drainage basin has an area of approximately 13 square miles. Both drainage basins discharge into Ebey Slough, which in turn discharges into Possession Sound. Historically, many of the tributary streams in the basins, especially the upper tributaries have been modified and straightened for agricultural purposes. Cross culverts have been installed at roads and access points. Both drainage basin surface waters flow generally in a northwesterly direction in the upper reaches of the tributaries, and a southwesterly direction in the lower reaches. 16THAVE NW132ND ST NE 99TH AVE NESR 52834TH AVE NE79TH AVE NE71ST AVE NESR 92 76TH ST NE 84TH ST NE SR 980TH ST NE ASH AVE116TH ST NE SR 984TH ST NE 52NDST NESHOULTES RD132ND ST NE 108TH ST NE SR 531 67TH AVE NE SMOKEY POINT BLVDI-5 I-551ST AVE NE88TH ST NE 67TH AVE NE 51ST AVE NE I-523RDAVE NEARMARRD140TH ST NE 48TH DR NE136TH ST NE FORTY-FIVE RD3RD AVE NE44TH ST NESUNN YSIDE BLVDSR 52927TH AVE NECEDAR AVE4TH ST47TH AVE NE100TH ST NE51ST AVE NEMARINE DR152ND ST NE 83RD AVE NEGROVE ST 64TH ST NE 172ND ST NE STATE AVE67TH AVE NESR 9I-5 LAKEWOOD RD SR 53 1M ARINE D R Quilceda CreekBasin Allen CreekBasinMu n s o n Cr e e kAllen CreekOlaf Strad Mission CreekQ uilce d a C reek P orta g e Creek Fish Creek Hayho CreekC ath erin e Cre e k Hulbert CreekKing CreekMiddle Fork Quilceda Creek Sturgeon CreekJones CreekWe st F ork Q uilc e d a C re e k Little Coho Edgecomb Creek Quilceda CreekCre e k Quilceda-Allen Watershed Sewer Service Area (UGA) Future planning areas Sewer Comprehensive Plan Fig 2-6 Watersheds 0 1 20.5 Miles 2-6 City of Marysville November 2011 Sewer Comprehensive Plan Section 303(d) of the federal Clean Water Act requires Washington State periodically to prepare a list of all surface waters in the state for which beneficial uses of the water such as for drinking, recreation, aquatic habitat, and industrial use which are impaired by pollutants. These are water quality limited estuaries, lakes, and streams that fall short of state surface water quality standards, and are not expected to improve within the next two years. Waters placed on the 303(d) list require the preparation of Total Maximum Daily Loads (TMDLs), a key tool in the work to clean up polluted waters. TMDLs identify the maximum amount of a pollutant to be allowed to be released into a waterbody so as not to impair uses of the water, and allocate that amount among various sources. In addition, even before a TMDL is completed, the inclusion of a water on the 303(d) list can reduce the amount of pollutants allowed to be released under permits issued by Ecology. Ecology’s assessment of which waters to place on the 303(d) list is guided by federal laws, state water quality standards, and the state’s 303(d) policy. This policy describes how the standards are applied, requirements for the data used, and how to prioritize TMDLs, among other issues. The goal is to make the best possible decisions on whether each body of water is impaired by pollutants, to ensure that all impaired waters are identified and that no waters are mistakenly identified. The Allen Creek is listed under section the current 303(d) (2008) and the proposed 2010 303(d) list for impairment from oxygen and pH. The Quilceda Creek is listed under section 303(d) for impairment from dissolved oxygen. Ebey Slough is listed for fecal coliform. There are also existing TMDLs for the Snohomish River Estuary (ammonia, CBOD, dissolved oxygen) and the Snohomish River tributaries (fecal coliform). Classification of marine waters changed in the 2006 water quality standard revisions (WAC 173-201A). Port Gardner Bay is classified “excellent quality” – the sloughs fall under marine water or freshwater standards according to their salinity levels, and streams flowing into the sloughs are probably freshwater. Ebey slough is classified as a Class A marine surface water, which is defined as having excellent quality. Fish and Wildlife Habitat The distribution of protected fish species was determined from Snohomish County wildlife habitat maps. Bull Trout are known to be present in the Snohomish River as well as Ebey Slough and Union Slough. It is presumed that they are also present in Allen Creek and Quilceda Creek. It is also known that Chinook Salmon are present in the Snohomish River, Ebey Slough, Union Slough, Allen Creek, and Quilceda Creek. WATER SYSTEM The Marysville water system was first established in the 1930s and is owned and operated by the City of Marysville. The system currently consists of 292 miles of pipe, seven reservoirs, one clearwell, one standpipe, three booster pump stations, 29 pressure reducing valves, and eight pressure zones. The City served 19,234connections in 2009 City of Marysville 2-7 Sewer Comprehensive Plan November 2011 for a population of 56,000 people. The 2009 Water System Plan uses a standard of 188 gallons per day per ERU for estimating future water demand. The sources of supply include Edward Springs (a spring and three wells), Stillaguamish Ranney Collector Well, Lake Goodwin Well, and an intertie to the City of Everett water system through the Everett-Marysville pipeline. The City also has two secondary sources of supply including the Highway 9 Well and Sunnyside Well No 2. When the water system first began operation in the 1930s, the source of supply was Edward Springs with an initial water right of 0.5 mgd. Later applications provided additional rights up to 2.0 mgd. The Sunnyside well was brought online in the 1950s and 1960s, Lake Goodwin came online in 1970, the City began withdrawing water from the Stillaguamish River in 1978, and Highway 9 Well was constructed in 1981. Under a 1991 Joint Operating Agreement, Marysville began receiving wholesale treated water from the City of Everett. The total capacity of the Everett-Marysville pipeline is 20 mgd, of which Marysville receives 11.3 mgd. The Stillaguamish River Ranney Well Collector has the ability to supply its full water right of 3.2 mgd. In 2006, the City constructed the Stillaguamish Water Treatment Plant to treat the Ranney Well Collector source water, primarily due to turbity, thereby allowing year round operation and allowing full use of the water right. Table 2-2 is a list of water system projects from the City of Marysville 2009 Six-Year Capital Improvement Plan (CIP). The list is included to coordinate with sewer capital projects that may be identified in this Plan. The City may potentially reduce project costs by installing both water and sewer pipeline as part of one project when it is feasible to do so. 2-8 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 2-2 2009 to 2014 Water System Capital Improvements Project No. Project Title Water Supply and Treatment WS-1 Additional Spring Collector Improvements WS-2 Lake Goodwin Well Development WS-3 Sunnyside Well #1 Relocate & #2 Rehab WS-4 Ultraviolet Treatment Water Storage ST-1 Edward Springs Baffles ST-2 Hwy 9 Reservoir Demolition ST-3 Hwy 9 Reservoir ST-4 Soper Hill (Whiskey Ridge) Property & Reservoir (1 MG) ST-5 North 510 Zone Reservoir (1 MG) Water Booster Pump Stations PS-1 Edward Springs Pump Modification PS-2 Edward Springs Booster Pump Building PS-3 Cedarcrest Pump Station Rehab (Motor Control/Valve Replacement) PS-4 Soper Hill (Whiskey Ridge) Pump Station (Design Point=700 gpm @ 130'; 35 hp) PS-5 North 510 Zone Pump Station (Design Point=300 gpm @ 300'; 40 hp) Water Transmission and Distribution System WD-1 State Ave (102nd to 116th; 4,578', replace 12" AC with 18" DI) WD-2 67th Ave (100th to 132nd; 10,469', new 18") and PRV WD-3 83rd Ave NE (60th to 64th; 1,301', upsize 12" to 16") WD-4 67th Ave NE (52nd to 64th; 3,943', upsize 10" to 16") WD-5 51st Avenue (119th Pl NE to 122nd Pl NE; 820', replace 12" CI with 12" DI) WD-6 Ebey Slough Bridge (717', new 12") WD-7 Cedar Avenue 1st - 5th (1,407', new 8") WD-8 Quinn Avenue 6th - 8th (972', new 8") WD-9 67th Ave NE (44th to 52nd); 44th St NE (67th to 71st); 71st Ave NE (to Sunnyside Res) (4,697', new 18") WD-10 140th Pl NE (23rd to I-5); north on 23rd Ave NE, then northwest on 45 Road (144th to 156th) (10,053', replace 12" AC with 18" DI) WD-11 71st Ave NE (52nd to 72nd; 6,559', 12") WD-12 52nd St NE (67th to 73rd; 2,023', replace 10" with 12") WD-13 Soper Hill (Whiskey Ridge) Reservoir waterline (4,378', new 12") WD-14 Soper Hill (Whiskey Ridge) PRVs (3) WD-15 Connection of Soper Hill to 360 Zone on 49th St NE (200', new 8") WD-16 83rd Ave NE (Soper Hill Res to 60th St; 6,859', new 16") WD-17 North 510 Zone Reservoir waterline (22,838', new 12") City of Marysville 2-9 Sewer Comprehensive Plan November 2011 TABLE 2-2… (continued) 2009 to 2014 Water System Capital Improvements Project No. Project Title Water Transmission and Distribution System WD-18 52nd Dr NE (north from 81st Pl NE to existing 6" CI; 340', new 8") WD-19 77th Pl NE (600', replace 6" with 8"); 76th St NE (410', replace 6" with 8") WD-20 60th Dr NE (3,842', upsize from 6" to 8") WD-21 61st Dr NE and 84th Pl NE (758', upsize from 6" to 8") WD-21 87th St NE (621', upsize from 6" to 8") WD-21 86th St NE (855', upsize from 6" to 8") WD-22 50th Ave NE (250', upsize from 6" to 8") WD-23 92nd St NE (561', upsize from 6" to 8") WD-24 134th Pl NE and 54th Dr NE (1,502', upsize from 6" to 8" and some new 8") WD-25 140th Pl NE (305', upsize from 4" to 8") WD-26 Pipes and valves to adjust North/South boundary (5 segments, 25' ea, 8") Water Maintenance and Operations WM-1 Watermain R&R WM-2 Watermain Oversizing WM-3 PRV Rate of Flow WM-4 Stillaguamish Fiber Optics WM-5 Water Meter AMR WM-6 Water System Plan Update 2-10 City of Marysville November 2011 Sewer Comprehensive Plan OTHER PUBLIC UTILITIES Telephone service in the area is provided by Frontier, and Cable TV by Comcast. Power service in the area is provided by Snohomish County Public Utility District (PUD) #1. Natural gas is provided by Puget Sound Energy. Nearby public wastewater treatment plants are operated by the Cities of Arlington, Granite Falls, Everett, and the Lake Stevens Sewer District. A private wastewater treatment plant is operated by the Tulalip Tribe. City of Marysville 3-1 Sewer Comprehensive Plan November 2011 CHAPTER 3 LAND USE AND PLANNING CRITERIA INTRODUCTION Specific land uses, such as residential and commercial developments, provide flows and loadings to the City’s wastewater treatment facilities. In addition, the configuration of the sewer system is based on growth projections, development trends, political considerations, topography, and the drainage characteristics of the area. Based on the City’s growth history and the need to provide wastewater treatment facilities services for future growth, the wastewater treatment and sewer systems are in need of continuous evaluation and improvement. This Chapter provides information relating to land use and associated zoning designations, existing and projected population, and the City’s growth history. These data are used in later chapters to evaluate if the City’s wastewater and sewer facilities are adequate to serve future growth and to meet regulatory requirements to the year 2031. In addition, buildout population is developed in this Chapter for a long-term assessment of the City’s collection system. PLANNING PERIOD The planning period for the City’s wastewater system should be long enough to be useful for an extended period of time, but not so long to be impractical. This Plan includes 6-year, and 20-year planning periods to allow for the implementation of the City’s capital improvement program. The 6-year planning period extends to the year 2017. The City of Marysville’s current Comprehensive Plan sets the 20-year planning period to the year 2025, which is consistent with Snohomish County Planning. This Plan will extend the capital improvement program to the year 2031. GROWTH MANAGEMENT The Growth Management Act (GMA) was enacted in 1990 to address the population growth that occurred in areas of Washington State during the 1980s. To ensure a continuation of Washington’s high quality of life, officials across the state have addressed growth management within various levels of government. The basic objective of the GMA is to encourage local county and city governments to develop and implement a 20-year comprehensive plan that incorporates their vision of the future within the framework of the broader needs of the state. Under the GMA, cities within a county must complete their own planning and coordinate the planning efforts with those of the county. The planning effort of a city includes the 3-2 City of Marysville November 2011 Sewer Comprehensive Plan establishment of an Urban Growth Area (UGA). The City established its first UGA in 1996, and also a planning area to accommodate future growth of the UGA. LAND USE AND ZONING The City of Marysville Municipal Code (MMC), Title 22, Unified Development Code , provides density and design requirements for the main land use categories within the City’s corporate boundaries and UGA, including residential, business, commercial, mixed use, industrial, business park, recreation and public/institutional, as shown on Figure 3-1. The City has five planning areas outside the UGA, each of which fall under the jurisdiction of Snohomish County’s zoning regulations. A description of the individual planning areas follows: • Planning Area #1: This area is generally located north of 90th Street NE, east of the eastern Marysville UGA boundary, south of 132nd Street NE and west of SR 9. This area is comprised of R-5 (1 d.u. per 5-acres) and A-10 (1 d.u. per 10-acres) zoning designations. • Planning Area #2: This area is generally located north of 132nd Street NE, east of the eastern Marysville UGA boundary, south of 172nd Street NE and west of SR 9. This area is comprised of R-5 (1 d.u. per 5-acres) and A-10 (1 d.u. per 10-acres) zoning designations. • Planning Area #3: This area is generally located north of the northern Marysville UGA boundary at approximately 17600 Block, east of 3rd Avenue NE, south of Portage Creek and west of I-5. This area is comprised of R-5 (1 d.u. per 5-acres) and RC (rural conservation) zoning designations. • Planning Area #4: This area is generally located north 140th Street NE, east of Forty-Five Road, south of SR 531 and west of the Marysville UGA boundary. This area is comprised of R-5 (1 d.u. per 5-acres) zoning designation. • Planning Area #5: This area is generally located north of 140th Street NE, east of 4th Avenue NW, south of SR 531 and west of Forty-Five Road. This area is comprised of R-5 (1 d.u. per 5-acres) zoning designation. The development densities listed above for each planning area may change if they become part of the City’s UGA. For the purposes of this Plan, the Planning Areas noted above along with the existing UGA will be referred to as the Ultimate Planning Area (UPA). CITY OF MARYSVILLE The purpose of designating land use within the City is to guide development to meet land use regulations and implement the land use goals identified in the City’s Comprehensive Plan. These land use designations apply to the City’s corporate boundaries and UGA, 132ND ST NE 99TH AVE NESR 52834TH AVE NE79TH AVE NE71ST AVE NESR 92 76TH ST NE 84TH ST NE SR 980TH ST NE ASH AVE116TH ST NE SR 984TH ST NE 52NDST NESHOULTES RD132ND ST NE 108TH ST NE SR 531 67TH AVE NE SMOKEY POINT BLVDI-5 I-551ST AVE NE88TH ST NE 67TH AVE NE51ST AVE NEI-523RDAVE NEARMARRD140TH ST NE 48TH DR NE136TH ST NE FO R T Y - F I V E R D3RD AVE NE44TH ST NESUNNYSIDE BLVDSR 52927TH AVE NECEDAR AVE4TH ST47TH AVE NE100TH ST NE51ST AVE NEMARINE DR152ND ST NE 83RD AVE NEGROVE ST 64TH ST NE 172ND ST NE STATE AVE67TH AVE NESR 9I-5 General Commercial Downtown Commercial Community Business Business Park Neighborhood Business Mixed Use 88 - Mixed Use General Industrial Light Industrial R28 Multi-Family High R18 Multi-Family Medium R12 Multi-Family Low R6-18 Multi-Family Low R8 Single Family High Small Lot R6.5 Single Family High R4-8 Single Family High R4.5 Single Family Medium Public-Institutional Recreation Open Sewer Comprehensive Plan Marysville ZoningFigure 3-1 0 1 20.25 0.5 0.75 Miles City of Marysville 3-3 Sewer Comprehensive Plan November 2011 while Snohomish County land use designations apply to the planning areas outside of the UGA. The boundaries for these areas are shown on Figure 3-1, Existing Zoning. MMC 22C.010.020 and MMC 22C.020.020 includes the following zoning designations within the City of Marysville. Density limits are provided for the residential zones. TABLE 3-1 City of Marysville Zoning Designations Zone Land Use Designation Residential Density (dwelling units per acre) R-4.5 Medium density single-family 4.5 R-6.5 High density single-family 6.5 R-8 High density single-family, small lots 8 WR R-4-8 Whiskey Ridge, high density single-family 4.5-8 R-12 Low density multiple-family 12-18 R-18 Medium density multiple-family 18-28 R-28 High density multiple-family 28-36 WR R-6-18 Whiskey Ridge, medium density multiple-family 6-18 NB Neighborhood Business CB Community Business 12 (1) GC General Commercial 12 (1) DC Downtown Commercial 12 (1) MU Mixed Use 28 LI Light Industrial GI General Industrial BP Business Park REC Recreation P/I Public/Institutional WR-MU Whiskey Ridge Mixed Use 12 WR-CB Whiskey Ridge Community Business (1)All units must be located above a street-level commercial use. At the time of development all residential, commercial, business, and industrial zoning designations must be served by public sewers, water, roads, and other needed public facilities and services. 3-4 City of Marysville November 2011 Sewer Comprehensive Plan Residential Zones The purpose of the residential zone (R) is to implement comprehensive plan goals and policies for housing quality, diversity and affordability, and to efficiently use residential land, public services and energy. These purposes are accomplished by: (1) Providing, in the R-4.5, R-6.5, and R-8 zones, for a mix of predominantly single detached dwelling units and other development types, with a variety of densities and sizes in locations appropriate for urban densities; (2) Providing, in the R-12, R-18, and R-28 zones, for a mix of predominantly apartment and townhome dwelling units and other development types, with a variety of densities and sizes in locations appropriate for urban densities; (3) Providing and preserving high density, affordable detached single-family and senior housing, in the R-MHP zone. This zone is assigned to existing mobile home parks within residential zones which contain rental pads, as opposed to fee simple owned lots, and as such are more susceptible to future development. (4) Allowing only those accessory and complementary nonresidential uses that are compatible with residential communities; and (5) Establishing density designations to facilitate advanced area-wide planning for public facilities and services, and to protect environmentally sensitive sites from overdevelopment. Use of this zone is appropriate in residential areas designated by the comprehensive plan as follows: (1) Urban lands that are served at the time of development, by adequate public sewers, water supply, roads and other needed public facilities and services; and (2) The corresponding comprehensive plan designations are as follows: R-4.5 = Medium density single-family R-6.5 = High density single-family R-8 = High density single-family, small lot R-12 = Low density multiple-family R-18 = Medium density multiple-family R-28 = High density multiple-family Neighborhood Business Zone The purpose of the neighborhood business zone (NB) is to provide convenient daily retail and personal services for a limited service area and to minimize impacts of commercial activities on nearby properties. These purposes are accomplished by: (1) Limiting nonresidential uses to those retail or personal services which can serve the everyday needs of a surrounding residential area; (2) Allowing for a mix of housing and retail/service uses; and (3) Excluding industrial and community/regional business-scaled uses. Use of this zone is appropriate in neighborhood centers designated by the comprehensive plan which are served at the time of development by adequate public sewers, water supply, roads and other needed public facilities and services. City of Marysville 3-5 Sewer Comprehensive Plan November 2011 Community Business Zone The purpose of the community business zone (CB) is to provide convenience and comparison retail and personal services for local service areas which exceed the daily convenience needs of adjacent neighborhoods but which cannot be served conveniently by larger activity centers, and to provide retail and personal services in locations within activity centers that are not appropriate for extensive outdoor storage or auto-related and industrial uses. These purposes are accomplished by: (1) Providing for limited small-scale offices as well as a wider range of the retail, professional, governmental and personal services than are found in neighborhood business areas; (2) Allowing for a mix of housing and retail/service uses; and (3) Excluding commercial uses with extensive outdoor storage or fabrication and industrial uses. Use of this zone is appropriate in community commercial areas that are designated by the comprehensive plan and are served at the time of development by adequate public sewers, water supply, roads and other needed public facilities and services. General Commercial Zone The purpose of the general commercial zone (GC) is to provide for the broadest mix of commercial, wholesale, service and recreation/cultural uses with compatible storage and fabrication uses, serving regional market areas and offering significant employment. These purposes are accomplished by: (1) Encouraging compact development that is supportive of transit and pedestrian travel, through higher nonresidential building heights and floor area ratios than those found in CB zoned areas; (2) Allowing for outdoor sales and storage, regional shopping areas and limited fabrication uses; and (3) Concentrating large-scale commercial and office uses to facilitate the efficient provision of public facilities and services. Use of this zone is appropriate in general commercial areas that are designated by the comprehensive plan that are served at the time of development by adequate public sewers, water supply, roads and other needed public facilities and services. Downtown Commercial Zone The purpose of the downtown commercial zone (DC) is to provide for the broadest mix of comparison retail, service and recreation/cultural uses with higher density residential uses, serving regional market areas and offering significant employment. These purposes are accomplished by: (1) Encouraging compact development that is supportive of transit and pedestrian travel, through higher nonresidential building heights and floor area ratios than those found in GC zoned areas; (2) Allowing for regional shopping areas, and limited fabrication uses; and (3) Concentrating large-scale commercial and office uses to facilitate the efficient provision of public facilities and services. 3-6 City of Marysville November 2011 Sewer Comprehensive Plan Use of this zone is appropriate in downtown commercial areas that are designated by the comprehensive plan that are served at the time of development by adequate public sewers, water supply, roads and other needed public facilities and services. Mixed Use Zone The purpose of the mixed use zone (MU) is to provide for pedestrian and transit-oriented high-density employment uses together with limited complementary retail and higher density residential development in locations within activity centers where the full range of commercial activities is not desirable. These purposes are accomplished by: (1) Allowing for uses that will take advantage of pedestrian-oriented site and street improvement standards; (2) Providing for higher building heights and floor area ratios than those found in the CB zone; (3) Reducing the ratio of required parking to building floor area; (4) Allowing for on-site convenient daily retail and personal services for employees and residents; and (5) Minimizing auto-oriented, outdoor or other retail sales and services which do not provide for the daily convenience needs of on-site and nearby employees or residents. Use of this zone is appropriate in areas designated by the comprehensive plan for mixed use, or mixed use overlay, which are served at the time of development by adequate public sewers, water supply, roads and other needed public facilities and services. Light Industrial Zone The purpose of the light industrial zone (LI) is to provide for the location and grouping of non-nuisance-generating industrial enterprises and activities involving manufacturing, assembly, fabrication, processing, bulk handling and storage, research facilities, warehousing and limited retail uses. It is also a purpose of this zone to protect the industrial land base for industrial economic development and employment opportunities. These purposes are accomplished by: (1) Allowing for a wide range of industrial and manufacturing uses; (2) Establishing appropriate development standards and public review procedures for industrial activities with the greatest potential for adverse impacts; and (3) Limiting residential, institutional, service, office and other nonindustrial uses to those necessary to directly support industrial activities. Use of this zone is appropriate in light industrial areas designated by the comprehensive plan which are served at the time of development by adequate public sewers, water supply, roads and other needed public facilities and services. General Industrial Zone The purpose of the general industrial zone (GI) is to provide for the location and grouping of industrial enterprises and activities involving manufacturing, assembly, fabrication, processing, bulk handling and storage, research facilities, warehousing and heavy trucking and equipment but also for commercial uses having special impacts and regulated by other chapters of this title. It is also a purpose of this zone to protect the City of Marysville 3-7 Sewer Comprehensive Plan November 2011 industrial land base for industrial economic development and employment opportunities. These purposes are accomplished by: (1) Allowing for a wide range of industrial and manufacturing uses; (2) Establishing appropriate development standards and public review procedures for industrial activities with the greatest potential for adverse impacts; and (3) Limiting residential, institutional, service, office and other nonindustrial uses to those necessary to directly support industrial activities. Use of this zone is appropriate in general industrial areas designated by the comprehensive plan which are served at the time of development by adequate public sewers, water supply, roads and other needed public facilities and services. Business Park Zone The purpose of the business park zone (BP) is to provide for those business/industrial uses of a professional office, wholesale, and manufacturing nature which are capable of being constructed, maintained and operated in a manner uniquely designed to be compatible with adjoining residential, retail commercial or other less intensive land uses, existing or planned. Strict zoning controls must be applied in conjunction with private covenants and unified control of land; many business/industrial uses otherwise provided for in the development code will not be suited to the BP zone due to an inability to comply with its provisions and achieve compatibility with surrounding uses. Use of this zone is appropriate in business park areas designated by the comprehensive plan which are served at the time of development by adequate public sewers, water supply, roads and other needed public facilities and services. Recreation Zone The purpose of the recreation zone (REC) is to establish areas appropriate for public and private recreational uses. Recreation would permit passive as well as active recreational uses such as sports fields, ball courts, golf courses, and waterfront recreation, but not hunting. This zone would also permit some resource land uses related to agriculture and fish and wildlife management. This recreation zone is applied to all land designated as “Recreation” on the comprehensive plan map. Public/Institutional Zone The purpose of the public/institutional (P/I) land use zone is to establish a zone for governmental buildings, churches and public facilities. This public/institutional zone is applied to all land designated as “public/institutional” on the comprehensive plan map. 3-8 City of Marysville November 2011 Sewer Comprehensive Plan Whiskey Ridge The purpose of the whiskey ridge overlay zone (WR suffix to zone’s map symbol) is to create an urban community that provides an attractive gateway into Marysville and becomes a prototype for developing neighborhoods within the City. The WR suffix identifies those areas required to comply with the East Sunnyside/Whiskey Ridge Design Standards and Guidelines, and Streetscape Design Plan. SNOHOMISH COUNTY Snohomish County land use regulations apply to those areas outside of the Marysville corporate boundaries and UGA. The Snohomish County GMA Comprehensive Plan, August 1, 2010, provides land use designations. The land use designations that apply to the Marysville UPA are listed below in Table 3-2. The land use designations may change as these areas are included in the UGA. The City provides sewer services within the unincorporated Marysville UGA consistent with the City’s Comprehensive Plan. TABLE 3-2 Snohomish County Marysville UPA Future Land Use Designation(1) Zone Future Land Use Designation Residential Density R-7,200 Public/Institutional 5-6 d.u. per acre R-5 Rural Residential 1 d.u. per 5-acres basic RC Local Commercial Farmland N/A R-5 Rural Residential-5 1 d.u. per 5-acres A-10 Rural Residential-10 1 d.u. per 10-acres (1) Snohomish County Zoning, January 18, 2011, and GMA Comprehensive Plan Future Land Use Map, August 1, 2010. Urban Single-family Residential R-7,200 The intent and function of Single Family Residential zones is to provide for predominantly single family residential development that achieves a minimum net density of four dwelling units per net acre. These zones may be used as holding zones for properties that are designated Urban Medium-Density Residential, Urban High-Density Residential, Urban Commercial, Urban Industrial, Public/Institutional use (P/IU), or Other land uses in the comprehensive plan. Single family residential zones consist of Residential 7,200 sq. ft. (R-7,200), Residential 8,400 sq. ft. (R-8,400) and Residential 9,600 sq. ft. (R-9,600). City of Marysville 3-9 Sewer Comprehensive Plan November 2011 Rural Single-family Residential R-5 The intent and function of the Rural-5 Acre zone (R-5) is to maintain rural character in areas that lack urban services. The R-5 zone permits single-family development at a density of one (1) dwelling unit per five (5) acres. Other Zones, Rural Conservation (RC) The Other zones category consists of existing zoning classifications that are no longer primary implementing zones but may be used in special circumstances due to topography, natural features, or the presence of extensive critical areas. Other zones consist of Suburban Agriculture-1 Acre (SA-1), Rural Conservation (RC), Rural Use (RU), Residential 20,000 sq. ft. (R-20,000), Residential 12, 500 sq. ft. (R-12,500) and Waterfront beach (WFB). Resource Zones, Agricultural 10-Acre (A-10) The Resource zones category consists of zoning classifications that conserve and protect lands useful for agriculture, forestry, or mineral extraction or lands which have long-term commercial significance for these uses. The intent and function of the Agricultural-10 Acre zone is to protect agricultural lands and promote agriculture as a component of the County economy, protect and promote the continuation of farming in areas where it is already established and in locations where farming has traditionally been a viable component of the local economy and permit in agricultural lands, with limited exceptions, only agricultural land uses and activities and farm-related uses that provide a support infrastructure for farming, or that support, promote or sustain agricultural operations and production including compatible accessory commercial or retail uses on designated agricultural lands. 3-10 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 3-3 UGA Land Use Designation Acreage From Marysville Comprehensive Plan 2011 !" #$$%&’( #)%#)#$$*+,’,- +#$$*+’" +%+(!’, ./0%%+,1 ",- - /02#0##,- 3 ( 2+*%%%#+--" ,+%4 $+&.#)(’", ,+%4 $+&$-- +%4 $+&5 /0 -"- /+4 $+&5 /0 , /+4 $+&$(1!’- ’,+%4 $+&.#),’,! ’/+4 $+&5 /0 (1 ’ /+4 $+&5 /0 $++.#%,’ *%#( POPULATION To evaluate the wastewater system’s existing facilities and to determine requirements for future facilities, the City’s existing and future population has been estimated and is used to project future wastewater flows. EXISTING POPULATION The 2010 US Census data provided the population and number of housing units for the City of Marysville. Table 3-4 shows the City’s population by Census Tract, and Figure 3-2 shows the primary census tracts, covering the City and its UGA for 2010. On November 9, 2009, Marysville City Council adopted Ordinance No. 2792, approving the “Central Marysville Annexation,” with an effective date of December 30, 2009. The Central Marysville Annexation annexed almost the entire Marysville UGA, adding an additional 20,000 people to the city. The difference in population between the city limits and the UGA is approximately 200 people. 9400.01Pop. - 6462HU - 2512 527.01Pop. - 1518HU - 611 527.09Pop. - 3337HU - 1178 527.05Pop. - 7206HU - 2490 521.04Pop. - 3359HU - 1496 528.03Pop. - 5103HU - 1913 531.02Pop. - 4634HU - 1883 535.05Pop. - 4988HU - 1934 528.04Pop. - 6971HU - 2432 526.03Pop. - 2434HU - 915 531.01Pop. - 3715HU - 1389 535.09Pop. - 3909HU - 1545 527.07Pop. - 3554HU - 1207 528.05Pop. - 4332HU - 1803 529.04Pop. - 5442HU - 2079 529.03Pop. - 4079HU - 1797 535.04Pop. - 6383HU - 2706 528.06Pop. - 7049HU - 2403 527.08Pop. - 5344HU - 1744 535.07Pop. - 4726HU - 1651 529.06Pop. - 4445HU - 1713529.05Pop. - 4239HU - 1964 Sewer Service Area (UGA)Future planning areasCensus Tracts 2010Population per acre0.2703 - 0.74390.7440 - 1.8761.877 - 2.7212.722 - 4.9004.901 - 9.006 Sewer Comprehensive Plan Figure 3-2 Census Tracts 0 10.5 Miles City of Marysville 3-11 Sewer Comprehensive Plan November 2011 TABLE 3-4 2010 Population and Housing Units(1) Corporate Boundary (1) 2010 US Census The data in Table 3-4 indicates the City’s 2010 population was 60,183 with 22,423 housing units, equivalent to 2.68 persons per household. For determining the average household size the census bureau does not distinguish between single-family and multi-family housing. SCHOOLS MARYSVILLE SCHOOLS The Marysville School District has 22 schools and serves a student/staff population of 13,862. Each school and its student population are shown in Table 3-5. LAKEWOOD SCHOOLS The Lakewood School District has five (5) schools and serves a student/staff population of 3,625. Each school and its student population is shown in Table 3-6. 3-12 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 3-5 Marysville School District Student and Staff Population: 2002 - 2010 School Population 2002 2003 2010 Elementary Schools Allen Creek 677 680 648 Cascade 559 574 504 Grove - - 550 Kellogg-Marsh 709 736 576 Liberty 477 483 552 Marshall 589 497 456 Pinewood 596 618 528 Quil Ceda 303 335 528 Shoultes 489 555 420 Sunnyside 660 655 624 Tulalip 271 363 288 Subtotal 5,330 5,496 5,674 Middle Schools Cedarcrest 982 956 838 Marysville Junior High (Totem) 993 957 893 Marysville Secondary Campus - - 200** Marysville Middle School 1,082 1,070 1,000 Tenth Street School 156 166 -* Tulalip Heritage 73 72 -* Subtotal 3,286 3,221 2,931 High Schools Marysville-Pilchuck 2,764 2,978 1,888 Marysville Secondary Campus - - 500** Mountain View (formerly known as Marysville Alternative High School) 287 294 338 Getchell High School - - 1,331 Arts & Technology (new) 150 -* Subtotal 3,051 3,422 4,057 Total Students 11,667 12,139 12,662 Total Staff 1,200 1,200 1,200 TOTAL: Students & Staff 12,867 13,339 13,862 *See Marysville Secondary Campus. **The Marysville Secondary Campus includes the following schools co-located on one campus: Arts & Technology, Tulalip Heritage, and the 10th Street School. Grades 6-12 are served at the Marysville Secondary Campus. City of Marysville 3-13 Sewer Comprehensive Plan November 2011 TABLE 3-6 Lakewood School District Student and Staff Population: 2010 School Population Elementary Schools English Crossing 614 Cougar Creek 500 Lakewood 598 Subtotal 1,712 Middle Schools Lakewood Middle 843 Subtotal 843 High Schools Lakewood High 772 Subtotal 772 Total Students 3,327 Total Staff 298 TOTAL: 3,625 3-14 City of Marysville November 2011 Sewer Comprehensive Plan PROJECTED FUTURE POPULATION Table 3-6 presents population projections for both the City and the existing UGA through the year 2035. The projected population for the City in the year 2035 is 88,448. TABLE 3-7 Projected Population 2010-2035 (1) ","’"1,( ",,’,1 !, ",’1-!! ",(’1,"’ ",’1 , ",’’1- ",’’1"(" ",-’!1(( ",-"1’ ",!-,1!( ""-(1 ’, ",-1 ’! "-1 -- "(--1, "-1 ! "-!1 "" "’"1’’ "-,1 (" "1(! "!(1 ! "("1, "(,1!! "(1 "((’1-, "(-1 ( "(1 (1) From Snohomish County Tomorrow Vision 2040 Preliminary Growth Distribution Working Paper, May 12, 2011 City of Marysville 3-15 Sewer Comprehensive Plan November 2011 NEIGHBORHOOD POPULATION PLANNING In addition to the UGA population projections shown in Table 3-7, the City’s Community Development Department has prepared a population capacity analysis for 11 individual neighborhood planning areas as shown in Figure 3-3 and Table 3-8. Table 3-8 presents the additional number of housing units and the current additional population capacity as of 2011. For the analysis shown in Table 3-8, the City’s Community Development Department uses a unit occupancy rate of 3.0 persons per dwelling unit (DU) for single-family population and 2.0 persons per dwelling unit for multi-family. Census data presented in Tables 3-4 and 3-5 provides an average household size of 2.68 persons per household but does not distinguish between single-family and multi-family households. 132ND ST NE 99TH AVE NESR 52834TH AVE NE79TH AVE NE71ST AVE NESR 92 76TH ST NE 84TH ST NE SR 980TH ST NE ASH AVE116TH ST NE SR 984TH ST NE 52NDST NESHOULTES RD132ND ST NE 108TH ST NE SR 531 67TH AVE NE SMOKEY POINT BLVDI -5 I-551ST AVE NE88TH ST NE 67TH AVE NE51ST AVE NEI-523RDAVE NEARMARRD140TH ST NE 48TH DR NE136TH ST NE FORTY-FIVE RD3RD AVE NE44TH ST NESUNN YSIDE BLVDSR 52927TH AVE NECEDAR AVE4TH ST47TH AVE NE100TH ST NE51ST AVE NEMARINE DR152ND ST NE 83RD AVE NEGROVE ST 64TH ST NE 172ND ST NE STATE AVE67TH AVE NESR 9I-5 Getchell Smokey Point Downtown Marshall Pinewood Kellogg Marsh Lakewood Sunnyside Shoultes Jennings Park East Sunnyside Marysville NeighborhoodsDowntownEast SunnysideGetchellJennings ParkKellogg MarshLakewoodMarshallPinewoodShoultesSmokey PointSunnyside Marysville NeighborhoodsFigure 3-3 0 1 20.5 Miles Sewer Comprehensive Plan 3-16 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 3-8 UGA Additional Population Capacity(1) NEIGHBORHOOD ADDITIONAL SINGLE FAMILY HOUSING UNITS ADDITIONAL MULTI-FAMILY HOUSING UNITS ADDITIONAL SINGLE FAMILY POPULATION ADDITIONAL MULTI-FAMILY POPULATION TOTAL ADDITIONAL POPULATION CAPACITY % OF TOTAL Downtown 101 913 303 1,826 2,129 6.0% East Sunnyside 2,776 2,210 8,328 4,420 12,748 35.7% Getchell 1,451 23 4,353 46 4,399 12.3% Jennings Park 109 0 327 0 327 0.9% Kellogg Marsh 743 59 2,229 118 2,347 6.6% Lakewood 552 2,154 1,656 4,308 5,964 16.7% Marshall 376 1,293 1,128 2,586 3,714 10.4% Pinewood 232 249 696 498 1,194 3.3% Shoultes 253 0 759 0 759 2.1% Smokey Point 19 518 57 1,036 1,093 3.1% Sunnyside 347 0 1,041 0 1,041 2.9% Total 6,959 7,419 20,877 14,838 35,715 100.0% (1) Updated from City of Marysville/Snohomish County 2007 Capacity Analysis Gray & Osborne, Inc., Consulting Engineers City of Marysville 3-17 Sewer Comprehensive Plan November 2011 NON-UGA SEWERED AREAS There are three areas within the Rural Utility Service Area (RUSA) that are currently served by the sewer collection system but are located outside of the Urban Growth Area. Agreements covering these areas are included in Appendix B. Current and future population estimates presented in Table 3-7 do not include these areas. Population for each of these areas has been estimated from aerial photographs. Each area is briefly described below: • Smokey Point: A 504-acre area of Smokey Point is served by Marysville although it is located within the City of Arlington’s UGA. It is bounded by I-5 on the west, 180th Street NE on the north, 43rd Avenue NE on the east, and 164th Street NE on the south. Approximately 50 percent of this area is classified commercial with the remainder single-family residential. The estimated 2010 population for the Smokey Point area is 2,560. • Mountain View Shores: This subdivision is located at 104th Street NE west of I-5 and contains 36 lots. A private pump station serves this subdivision. The estimated 2010 population for the Mountain View Shore area is 84. • Tulalip Area: This area is located west of I-5 and is connected to the sewer system through the Marysville West Pump Station. This area contains the Tierra Bonita subdivision with about 240 lots, and a commercial area of the Tulalip Tribe, and two schools. The estimated 2010 population in the Tulalip area served by the sewer system is 1,038. The Tulalip Tribe has recently constructed a new treatment facility north of this area, which serves other parts of the Tulalip area. A purchase agreement for the Marysville West Pump Station is currently being negotiated between the City of Marysville and the Tulalip Tribes. Purchase of the pump station by the Tribes is anticipated to take place in the near future, therefore, this area may no longer be part of the City’s sewer system. 3-18 City of Marysville November 2011 Sewer Comprehensive Plan SEWER CONNECTIONS Table 3-9 provides the average number of sewer service connections by customer class for 2011, based on billing records provided by the City. As shown in Table 3-9, the number of sewer connections throughout 2011 was 18,421. The majority of the sewer service connections are in the City Single Family Residential (13,885 connections) and Rural Single Family Residential (2,932 connections) customer classes. The term City designates customers within the City limits, while Rural indicates customers outside the City limits but within the UGA. TABLE 3-9 2011 Sewer Service Connections RATE CODE DESCRIPTION CUSTOMERS S01 City Single Family Residential 13,885 S02 Rural Single Family Residential 2,932 S03 City Multi-Family 686 S04 Rural Multi-Family 40 S05 City Motel/Hotel 4 S06 Rural Motel/Hotel 5 S10 Rural Overnight Camping 1 S35 City Commercial Class 1 7 S38 City Commercial Class 2 20 S39 Rural Commercial Class 2 2 S41 City Commercial Class 3 655 S42 Rural Commercial Class 3 125 S50 City Commercial Class 6 3 S51 Rural Commercial Class 6 2 S53 City Class 3 Restaurant w/Surcharge 2 S54 Rural Class 3 Restaurant w/Surcharge 1 S55 City Restaurant w/o GT No Surcharge 17 S56 Rural Restaurant w/o GT No Surcharge 1 S60 Monthly Rural Class 3 2 S63 Monthly Rural Hotel/Motel 1 S65 School 30 TOTAL 18,421 City of Marysville 3-19 Sewer Comprehensive Plan November 2011 CURRENT SEWER SERVICE AREA POPULATION Table 3-10 provides the estimated average population connected to the sewer in 2011, based on City of Marysville billing records. As shown in Table 3-10, approximately 48,451 single-family and multi-family residents within the UGA have sewer service and approximately 2,092 single-family and multi-family residents located outside of the UGA, but within the UPA, have sewer service. The total estimated population served by the City of Marysville sewer system in 2011 is 50,543. TABLE 3-10 Marysville 2011 Estimated Sewer Service Population /+4 $+&,1""("!1-’ +%4 $+&1!!("!1’- /+4 $+&# ’("!,1’"- +%4 $+&#"! ."1 ( PROJECTED SEWER SERVICE AREA POPULATION The projected year 2017 and 2031 sewer service area population is summarized in Table 3-11. In developing these projections the following assumptions were made: • All of the currently unconnected population in the City limits connects to the sewer system by 2031 at a constant rate. • Half of the currently unconnected rural UGA population connects to the sewer system by 2031 at a constant rate. • The population growth within the UGA will follow the pattern presented in Tables 3-7 and 3-8. • All new single-family and multi-family residences within the City’s UGA will connect to the sewer system. 3-20 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 3-11 Projected Sewer Service Population Summary 2011 2017 2031 #3 +%#6 61,491 69,338 84,989 7 *#3 +%# *+/#66 ’1’’!-1’,’-1-- 7 *#3 +%# #*%%#)"1 (62,250 -1-- *%*23.16% -(’(8 *%#*%-8 ’8 ,""8 *UGA population from Snohomish County Tomorrow Vision 2040 Preliminary Growth Distribution Working Paper, May 12, 2011 **Service Area population taken from sewer model loading tables Ultimate Buildout Population Population projections presented in Tables 3-7 and 3-8 address current and future population for existing corporate City limits and UGA. The buildout population for the existing UGA is shown in the summary below: 60,183 (Existing population) + 35,715 (Additional population) 95,898 buildout population from UGA(1) (1) Information from the City of Marysville/Snohomish County 2007 Capacity Analysis. Future expansion of the UGA boundary would include the six planning areas identified on Figure 2-2. The UGA may be expanded to include part, or all of these areas. For the ultimate buildout population estimate, it is assumed that the UGA will include all six areas. The basis for the ultimate buildout population is a combination of net buildable acreage, allowable development density, and the population per dwelling unit. Each of these factors is discussed below for areas outside the current UGA boundary. City of Marysville 3-21 Sewer Comprehensive Plan November 2011 Net Acreage Each of the six planning areas shown in Figure 3-4 along with the “unbuildable” lands identified as steep slopes, wetlands, lakes and other critical areas. Removing the “unbuildable” lands from the total acreage leaves the maximum buildable acreage. The City’s Community Development Department estimates a net reduction factor of about 44 percent to allow for unbuildable lands, roads, public use, and right-of-ways. To reach this reduction factor, the maximum buildable acreage is reduced by 30 percent for roads, public use, and right-of-ways. Another adjustment covers Planning Area #5. This planning area is within the jurisdiction of the Tulalip Tribe. Only limited future development is expected consisting of “infill” of areas currently sewered. In addition to these reductions, Planning Areas #1 and #2 located north and east of the City are expected to remain substantially rural. According to the City’s Community Development Department, about 1,950 acres would develop only at 0.2 dwelling units per acre. Development Density Recent development trends favor smaller lot sizes (i.e., 3,500 square feet), which is equivalent to 8 to 10 dwelling units per acre. Actual development in the nearby rural areas of the Lake Stevens Sewer District is closer to 6.5 to 8.0 (average 7.25) dwelling units per acre due to lot averaging. For the ultimate buildout population, the development density will cover a range of 0.2 (rural) to a higher density of 7.25 dwelling units per acre. The majority of Planning Areas #1 and #2 will remain rural at 0.2 Du/acre. For the remainder of these two planning areas, a development density of 4.5 Du/acre will be utilized. A higher development density of 7.25 Du/acre will be utilized for Planning Areas #3, #4, and #6. Household Population For single-family residences, a rate of 3.0 person per household was used. For multi- family units, it is 2.0 persons per household. Table 3-12 incorporates each of the factors for net acreage, development density and household population to develop the ultimate buildout population. Including the existing UGA, areas served by agreements, and the planning areas, the estimated ultimate build out population is 161,554. As shown in Table 3-12, the total acreage is 10,436 acres with a net average of 6,015 acres, a reduction of 58 percent. 16THAVE NW132ND ST NE 99TH AVE NESR 52834TH AVE NE79TH AVE NE71ST AVE NESR 92 76TH ST NE 84TH ST NE SR 980TH ST NE ASH AVE116TH ST NE SR 984TH ST NE 52NDST NESHOULTES RD132ND ST NE 108TH ST NE SR 531 67TH AVE NE SMOKEY POINT BLVDI -5 I-551ST AVE NE88TH ST NE 67TH AVE NE 51ST AVE NE I -523RDAVE NEARMARRD140TH ST NE 48TH DR NE136TH ST NE FORTY-FIVE RD3RD AVE NE44TH ST NESUNN YSIDE BLVDSR 52927TH AVE NECEDAR AVE4TH ST47TH AVE NE100TH ST NE51ST AVE NEMARINE DR152ND ST NE 83RD AVE NEGROVE ST 64TH ST NE 172ND ST NE STATE AVE67TH AVE NESR 9I-5 E L AKE GOODWIN RDLAKEWO O D RD SR 53 1140TH ST NE M A RIN E DR City of Arlington City of Marysville City of Lake Stevens City of Everett Tulalip Indian Reservation GETCHELL1935 HU SMOKEY POINT608 HU DOWNTOWN1209 HU PINEWOOD1394 HU MARSHALL2796 HU KELLOGG MARSH1401 HU SUNNYSIDE420 HU SHOULTES810 HU JENNINGS PARK143 HU EAST SUNNYSIDE5518 HU LAKEWOOD2762 HU PLANNING AREA #22290 HU PLANNING AREA #310852 HU PLANNING AREA #12129 HU PLANNING AREA #66796 HU PLANNING AREA #44148 HU Sewer service area (UGA) City LimitsMarysville NeighborhoodsAdditional Plus Non-Sewer Housing Units 143 144 - 420 421 - 608 609 - 810 811 - 1209 1210 - 1394 1395 - 1401 1402 - 1935 1936 - 2762 2763 - 2796 2797 - 5518Future Planning AreasAdditional Housing Units 2129 2130 - 2290 2291 - 4148 4149 - 6796 6797 - 10852 City of MarysvilleSewer Comprehensive Plan 0 1 20.5 Miles Figure 3-4 Future Sewer Growth 3-22 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 3-12 2031 Capacity Population Planning Area Total Acres Buildable Acres Net Acres Density PPH Population #1 Low 1,653.6 1,258.9 881.3 0.2 2.6 458 #1 Medium 814.4 620.1 434.0 4.5 2.6 5,078 #2 Low 1,702.5 1,432.5 1,002.7 0.2 2.6 521 #2 Medium 838.5 666.6 466.6 4.5 2.6 5,459 #3 2,539.7 2,138.4 1,496.9 7.5 2.6 29,189 #4 903.1 817.3 572.1 7.5 2.6 11,156 #5 570.8 320.7 224.5 0.0 0.0 0 #6 1,413.1 1,339.0 937.3 7.5 2.6 18,277 Subtotal Planning Areas 70,140 UGA Capacity 88,032* Non-UGA 3,382 Total Capacity 161,554 * Snohomish County Buildable Lands Report 2007 City of Marysville 4-1 Sewer Comprehensive Plan November 2011 CHAPTER 4 REGULATORY REQUIREMENTS INTRODUCTION Regulatory requirements have been used in developing the design criteria for improvements to Marysville’s wastewater collection, treatment, and disposal systems. The purpose of this chapter is to identify and summarize the regulations that are applicable to the planning, design, and approval of the capital improvements discussed in this Plan. This Chapter does not describe each regulation in detail; rather, it addresses important elements of the regulations that affect the planning and design process. Subsequent sections of this Plan address technical requirements of the regulations at a level of detail appropriate for the evaluation provided by that section. For instance, Chapter 9 contains a discussion of biosolids regulations. FEDERAL AND STATE STATUTES, REGULATIONS AND PERMITS This section provides a summary of various state and federal laws that may affect wastewater system construction and operations, as well as other relevant permits, programs, and regulations. FEDERAL CLEAN WATER ACT The Federal Water Pollution Control Act is the principal law regulating the water quality of the nation’s waterways. Originally enacted in 1948, it was significantly revised in 1972 and 1977, when it was given the common title “Clean Water Act” (CWA). The CWA has been amended several times since 1977. The 1987 amendments replaced the Construction Grants program with the State Revolving Fund (SRF), which provides low- cost financing for a range of water quality infrastructure projects. The National Pollutant Discharge Elimination System (NPDES) is established by Section 402 and subsequent amendments of the CWA. The Department of Ecology (Ecology) administers NPDES permits for the United States Environmental Protection Agency (EPA). Most NPDES permits have a five-year life span and place limits on the quantity and quality of pollutants that may be discharged. The City’s current NPDES permit, No. WA002249-7, is attached as Appendix A. The City’s current NPDES permit effluent limits are shown in Table 5-6 in Chapter 5. 4-2 City of Marysville November 2011 Sewer Comprehensive Plan Condition S.2 of the City’s permit lists the WWTP’s required testing schedule. In addition to typical monitoring requirements such as influent and effluent flow, CBOD5, TSS, etc., the City must monitor for effluent ammonia and whole effluent toxicity. Condition S.4 of the NPDES permit requires the City to prepare a plan to maintain adequate capacity when flows and loadings to the WWTP exceed 85 percent of design capacity. Condition S.4 also specifies the design capacity of the WWTP. The WWTP’s design capacity for maximum month BOD5 loading is 20,143 lbs/day, and the design capacity for maximum month TSS loading is 24,229 lbs/day. The flow capacity for the WWTP is 12.7 million gallons per day (mgd). Section 303 of the CWA established the Total Maximum Daily Load (TMDL) program. Under this program, states must establish a list of water bodies that do not achieve water quality standards even with “all known available and reasonable technology (AKART)” in place. In such situations, Ecology conducts a TMDL analysis to determine the capacity of the water body to absorb pollutants and allocates pollutant loads among point and nonpoint discharges. Based on this loading capacity, “waste load allocations” are established for different pollutant sources within the watershed. Additional information about the effect of TMDLs on the City’s wastewater effluent discharge is provided later in this chapter. Section 307 of the CWA established the National Pretreatment Program. This program is designed to protect publicly owned treatment works (POTWs) and limits the amount of industrial or other non-residential pollutant discharged to municipal sewer systems. PROPOSED EPA CAPACITY, MANAGEMENT OPERATION AND MAINTENANCE REGULATIONS EPA has proposed a new round of regulations regarding sewer system Capacity, Management Operation and Maintenance (CMOM). Although the regulations have not been formally adopted by EPA, some municipalities are anticipating the adoption and have moved forward with implementation. CMOM focuses on the failure of collection systems to have a program for long-term finance and repair. This has resulted in sanitary sewer overflows (SSO) that EPA has proposed to address under its authority granted by the federal CWA. In general the CMOM requirements can be broken into the following areas: 1. General performance standards including system maps, information management, and odor control. 2. Program documentation including the goals, organizational and legal authority of the organization operating the collection system. City of Marysville 4-3 Sewer Comprehensive Plan November 2011 3. An overflow response plan, which requires response in less than one hour and is demonstrated to have sufficient and adequate personnel and equipment, etc. Estimated volumes and duration of overflows must be accurately measured and reported to the regulatory agency. 4. System evaluation requires that the entire system be cleaned on a scheduled basis (for example, once every 5 years), be regularly inspected through TV work and that a program for short and long term rehabilitation replacement be generated. EPA has proposed, as a rule of thumb, a 1-1/2 to 2 percent system replacement rate which implies that an entire collection system is replaced somewhere in the range of a 50 – 70 year time period. 5. A capacity assurance plan that will use flow meters to model I&I, ensure pump stations are properly operated and maintained and that source control is maintained. 6. A program for self-audit to evaluate and adjust performance. 7. A communication program to communicate problems, costs, and improvements to the public and decision-makers. EPA is considering some changes in design standards for collection systems including requiring that sanitary sewer overflows not occur except in extreme storms. They have also decided that they will not predefine what that type of storm is, leaving that decision to the design engineer. Proposed CMOM requirements are discussed in greater detail in Chapter 10. BIOSOLIDS Chapter 9 of this Plan provides a discussion of the regulatory requirements relating to biosolids treatment and management. FEDERAL ENDANGERED SPECIES ACT On March 24, 1999 the National Marine Fisheries Service (NMFS) listed the Puget Sound Chinook as “threatened” under the Endangered Species Act (ESA) and reaffirmed on June 28, 2005. National Oceanic and Atmospheric Administration (NOAA) Fisheries issued results of a five year review on August 15, 2011, and concluded that this species should remain listed as threatened. On June 10, 1998, the USFWS listed the Bull Trout as “threatened.” ESA listings are expected to significantly impact activities that affect salmon and trout habitat, such as water use, land use, construction activities, and wastewater disposal. 4-4 City of Marysville November 2011 Sewer Comprehensive Plan The National Marine Fisheries Service (NMFS) has listed a number of “Evolutionarily Significant Units” of chinook salmon. In addition, the United States Fish and Wildlife Service (USFWS) listed the Bull Trout as “threatened” during the summer of 1998. ESA listings are expected to significantly impact activities that affect salmon and trout habitat, such as water use, land use, construction activities, and wastewater disposal. Impacts to the greater Marysville area may include longer timelines for permit applications, and more stringent regulation of construction impacts and activities in riparian corridors. In response to existing and proposed ESA listings of salmon, steelhead, and trout species throughout Washington State, Governor Locke established the Office of Salmon Recovery in 1997 to direct the State’s salmon recovery efforts. Rather than attempting to avert additional ESA listings, the Statewide Strategy intends to provide local input into, and hopefully maintain some local control over the salmon recovery regulatory processes that will inevitably affect the majority of Washington State. The Statewide Strategy was submitted to NMFS in 1999 for possible inclusion in the Section 4(d) rule. Before 2000, NOAA Fisheries Service had simply adopted 4(d) rules that prohibited take of threatened species. In a salmon and steelhead 4(d) rule singed in July of 2000, the agency pioneered a new approach. It applied take prohibitions to all actions except those within 13 “limits” to the rules (described in detail in the rules) where the specified categories of activities contribute to conserving listed salmon. In order to minimize liability under the ESA, local governments need to demonstrate that their land use regulations will not result in a prohibited “take” of a listed species, including adverse modification of critical habitat. Impacts to the City may include longer timelines for permit applications, and more stringent regulation of construction impacts and activities in riparian corridors. Additionally, the City of Marysville’s wastewater treatment plant discharges to Steamboat Slough, a part of the Snohomish River system that flows into Puget Sound. Salmon and bull trout are expected to be present in the vicinity of the outfall and could potentially impact future WWTP and outfall modifications. In an effort to minimize the impact to critical fish habitat in Steamboat Slough, the City of Marysville constructed a pipeline to the City of Everett’s South End Pump Station during the 2004 treatment plant upgrades. From Everett’s pump station, the effluent is discharged to the Deep Marine Outfall in Port Gardner Bay. Marysville discharges all of its flow to Everett’s pump station during periods of low river flow (July through October). RECLAIMED WATER STANDARDS The standards for the use of reclaimed water are outlined in RCW 90.46 and in a separate document published by the Washington State Departments of Health and Ecology entitled “Water Reclamation and Reuse Standards.” Reclaimed water is the effluent derived in any part from wastewater from a wastewater treatment system that has been adequately and reliably treated, such that it is no longer considered wastewater and is suitable for a beneficial use or a controlled use that would not otherwise occur. The legislature has declared that “the utilization of reclaimed water by local communities for domestic, agricultural, industrial, recreational, and fish and wildlife habitat creation and City of Marysville 4-5 Sewer Comprehensive Plan November 2011 enhancement purposes (including wetland enhancement) will contribute to the peace, health, safety, and welfare of the people of the State of Washington.” RCW 90.48.112 requires consideration of reclaimed water in general sewer plans. Chapter 8 provides an evaluation of reclaimed water opportunities for the City of Marysville. The Water Reclamation and Reuse standards define the water quality standards for reclaimed water. A Class “A” reclaimed water treatment facility must meet four minimum requirements, as follows: Continuously Oxidized: Wastewater that at all times has been stabilized such that the monthly average BOD5 and TSS are less than 30 mg/L, is non- putrescable, and contains dissolved oxygen. Continuously Coagulated: Oxidized wastewater that at all times has been treated by a chemical equally effective method to destabilize and agglomerate colloidal and finely suspended mater prior to filtration. Continuously Filtered: Oxidized and coagulated wastewater that at all times has been passed through a filtering media so that the turbidity of the filtered effluent does not exceed an average of 2 nephelometric turbidity units (NTU), determined monthly, and does not exceed 5 NTU at any time. Continuously Disinfected: Oxidized, coagulated, and filtered wastewater that at all times has been disinfected to destroy or inactivate pathogenic organisms. A group of indicator microorganisms, coliform bacteria, are used to measure the effectiveness of the disinfection process. The Class “A” reclaimed water standard is a total coliform density of 2.2 per 100 milliliters (ml) for the median of the last seven days of samples, with no sample having a density greater than 23 per 100 ml. NATIONAL ENVIRONMENTAL POLICY ACT The National Environmental Policy Act (NEPA) was established in 1969 and requires federal agencies to determine environmental impacts on all projects requiring federal permits or funding. Federally delegated activities such as NPDES permits or Section 401 Certification are considered state actions and do not require NEPA compliance. If a project involves federal action (through, for example, an Army Corps of Engineers Section 404 permit), and is determined to be environmentally insignificant, a Finding of No Significant Impact (FONSI) is issued, otherwise an Environmental Impact Statement (EIS) is required. NEPA is not applicable to projects that do not include a federal component that would trigger the NEPA process. 4-6 City of Marysville November 2011 Sewer Comprehensive Plan FEDERAL CLEAN AIR ACT The Federal Clean Air Act requires all wastewater facilities to plan to meet the air quality limitations of the region. The City falls in the jurisdiction of the Puget Sound Clean Air Agency. An air quality permit for the City’s WWTP is not required. STATE STATUTES, REGULATIONS AND PERMITS STATE WATER POLLUTION CONTROL ACT The intent of the state Water Pollution Control Act is to “maintain the highest possible control standards to ensure the purity of all waters of the state consistent with public health and the enjoyment…the propagation and protection of wildlife, birds, game, fish, and other aquatic life, and the industrial development of the state.” Under the Revised Code of Washington (RCW) 90.48 and the Washington Administrative Code (WAC) 173-240, Ecology issues permits for wastewater treatment facilities and also land application of wastewater under WAC 246-271. Submission of Plans and Reports for Construction of Wastewater Facilities, WAC 173-240 Prior to construction or modification of domestic wastewater facilities, engineering reports and plans, and specifications must be submitted to and approved by Ecology. This regulation outlines procedures and requirements for the development of an engineering report, which thoroughly examines the engineering and administrative aspects of a domestic wastewater facility project. This regulation defines a facility plan as described in federal regulations, 40 CFR Part 35, as an engineering report. Key provisions of WAC 173-240 are provided below. • An engineering report for a wastewater facility project must contain everything required for a general sewer plan unless an up-to-date general sewer plan is on file with Ecology. • An engineering report shall be sufficiently complete so that plans and specifications can be developed from it without substantial changes. • A wastewater facility engineering report must be prepared under the supervision of a professional engineer. City of Marysville 4-7 Sewer Comprehensive Plan November 2011 Criteria for Sewage Works Design, Washington State Department of Ecology (Orange Book) Ecology has published design criteria for collection systems and wastewater treatment plants. While these criteria are not legally binding, their use is strongly encouraged by Ecology since the criteria are used by the agency to review engineering reports for upgrading wastewater treatment systems. These design criteria, commonly referred to as the “Orange Book,” primarily emphasize unit processes through secondary treatment, and also includes criteria for planning for, and design of, wastewater collection systems. Any expansion or modification of the City of Marysville’s collection system and/or treatment plant will require continued conformance with Ecology criteria. Certification of Operators of Wastewater Treatment Plants, WAC 173-230 Wastewater treatment plant operators are certified by the State water and wastewater operators’ certification board. The operator assigned for the overall responsibility of operation of a wastewater treatment plant is defined by WAC 173-230 as the “operator in responsible charge.” This individual must be State certified at or above the classification rating of the plant. The City’s wastewater treatment plant is currently assigned a Class III rating and the operating staff assigned to the plant has the required certification. WATER QUALITY STANDARDS FOR SURFACE WATERS OF THE STATE OF WASHINGTON, CHAPTER 173-201A WAC Basis of Regulations The State of Washington has authority under the federal Water Pollution Control Act, also known as the Clean Water Act (CWA), to establish and administer programs to meet the requirements of the CWA. Under RCW 98.40.35, the Washington Department of Ecology has the authority to establish “rules and regulations relating to standards of quality for waters of the State and for substances discharged therein...” The state of Washington also implements the NPDES program created under the CWA. Description of Regulations WAC 173-201A establishes water quality standards within the state of Washington. The State adopted revised water quality standards in 2006. The standards are based on two objectives: protection of public health and enjoyment, and protection of fish, shellfish, and wildlife. For each surface water body in the state, the revised standards assign specific uses, such as aquatic life, recreation, or water supply. Water quality standards have been developed for each use, for parameters such as fecal coliform, dissolved oxygen, temperature, pH, turbidity, and toxic, radioactive, deleterious substances. The water uses that are defined in the standards for freshwater are summarized as follows: 4-8 City of Marysville November 2011 Sewer Comprehensive Plan Aquatic life uses • Char • Salmon and trout spawning, core rearing, and migration • Salmon and trout spawning, non-core rearing, and migration • Salmon and trout rearing and migration only • Non-anadromous interior redband trout • Indigenous warm water species Recreational uses • Extraordinary primary contact recreation • Primary contact recreation • Secondary contact recreation Water supply uses • Domestic water supply • Agricultural water supply • Industrial water supply • Stock watering Miscellaneous uses • Wildlife habitat • Harvesting • Commerce and navigation • Boating • Aesthetics The water uses that are defined in the standards for marine waters include: Aquatic life uses • Extraordinary quality • Excellent quality • Good quality • Fair quality Shellfish harvesting and Recreational uses • Primary contact recreation • Secondary contact recreation City of Marysville 4-9 Sewer Comprehensive Plan November 2011 Miscellaneous uses • Wildlife habitat • Harvesting • Commerce and navigation • Boating • Aesthetics Water Quality Classification One of the City’s discharge locations is to Steamboat Slough that is a tributary of the Snohomish River. The Snohomish River is classified in WAC 173-201A-602 as having the following uses: • Aquatic Life Use: Non-core salmon/trout rearing and migration • Recreation Use: Primary contact recreation • Water Supply Uses: Domestic water supply, agricultural water supply, industrial water supply, stock watering • Miscellaneous Uses: Wildlife habitat, harvesting, commerce/navigation, boating, and aesthetics Water quality criteria for the salmon and trout spawning use is shown in Table 4-1: TABLE 4-1 Water Quality Criteria for the Salmon and Trout Spawning, Non-core Rearing and Migration Use Parameter Surface Water Criteria Value Dissolved Oxygen >8.0 mg/L Temperature 17.5 degrees C (7-day average of daily maximum), (1) with no increase greater than t=28/(T+5) or (2) if natural temperature is >17.5 degrees C, then no increase >0.3 degrees C pH Not outside the range of 6.5 to 8.5 standard units, with no human- caused variation >0.5 standard units Turbidity <5 NTU over background (background <50 NTU) <10 percent increase over background (background >50 NTU) Total dissolved gas <110 percent of saturation The bacterial water quality criteria for the Snohomish River, as shown in Table 4-2, is based on the assigned recreational use for freshwater. 4-10 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 4-2 Water Quality Criteria for the Freshwater Primary Contact Recreational Use Parameter Surface Water Criteria Value Fecal Coliform 100 fecal coliform colonies/100 mL Water supply and miscellaneous uses do not have additional numerical criteria. The water quality standards also have narrative criteria regarding toxic, radioactive, otherwise deleterious materials, or materials that impair aesthetics. These materials are prohibited in concentrations that affect aquatic life, human health, or impair aesthetics. Numeric criteria for 29 toxic substances are listed in WAC 173-201A-040. Criteria are listed for both an acute and chronic basis and for certain substances (e.g., metals, chlorine, and ammonia), the criteria must be calculated as a function of receiving water pH, hardness, and whether salmonids are present. The water quality standards allow for variances and site-specific criteria to be developed on an individual basis. To remove a use from the list of uses for which a water body is protected, a use attainability analysis (UAA) must be performed. The UAA must demonstrate that the use does not exist in the water body or would not be attainable. The proposed change to the assigned uses must be consistent with federal laws and subject to a public involvement process and include a consultation with tribes. Mixing Zones WAC 173-201A-100 has provisions for mixing zones for a permitted discharge. Deviations from water quality standards for the surface water are allowed within the mixing zone. Mixing zones are allowed under the following conditions: 1. All known, available, and reasonable treatment (AKART) technology is applied prior to discharge to the mixing zone. 2. Water quality is not violated outside the mixing zone boundary. 3. When the potential does not exist for damage to sensitive ecosystem or aquatic habitat, adverse public health effects, or interference with characteristic uses of the water. 4. Chronic toxicity criteria are met within a mixing zone that does not exceed 25 percent of the river width, use more than 25 percent of the river flow, City of Marysville 4-11 Sewer Comprehensive Plan November 2011 and does not extend more than 100 ft upstream or 300 ft downstream (plus the depth of water over the discharge port). 5. Acute toxicity criteria are met within a mixing zone that does not exceed 2.5 percent of the river flow, does not occupy more than 2.5 percent of the width of the river, and does not extend beyond 10 percent of the distance towards the upstream and downstream boundaries of an authorized mixing zone. The City’s mixing zone is described in its NPDES Permit No. WA-002249-7 included in Appendix A. Anti-degradation policy The anti-degradation policy aims to maintain the highest possible quality of water in the State, by preventing the deterioration of water bodies that currently have higher quality than the water quality standards require. The revised water quality standards define three tiers of waters in the anti-degradation policy. Tier I water bodies are those with violations of water quality standards, from natural or human-caused conditions. The focus of water quality management is on maintaining or improving current uses, and preventing any further human-caused degradation. Tier II water bodies are those of higher quality than required by the water quality standards. The focus of the policy is on preventing degradation of the water quality and to preserve the excellent natural qualities of the water body. New or expanded actions are not allowed to cause a “measurable change” in the water quality, unless they are demonstrated to be “necessary and in the overriding public interest.” New or expanded actions that may cause a measurable change in water quality must conduct a Tier II review. For increased wastewater treatment plant discharges, this review will take place as part of the NPDES permit modification process. Measurable change, for the purpose of the anti-degradation policy, is defined as follows: • Temperature increase greater than 0.3 degrees C • Dissolved oxygen concentration decrease greater than 0.2 mg/L • Bacteria level increase greater than 2 CFU/100 mL • pH change greater than 0.1 standard units • Turbidity increase greater than 0.5 NTU • Any detectable change in concentration of toxic or radioactive substances, which include ammonia and chloride. A new or expanded action may be determined by the Ecology to be necessary and in the overriding public interest based on a review of the following factors: 4-12 City of Marysville November 2011 Sewer Comprehensive Plan • Economic benefits, such as job creation • Providing or contributing to necessary social services • Status as a demonstration project using innovative technical or management approaches that produce a significant improvement over AKART • Prevention or remediation of environmental or public health threats • Societal or economic benefits of better health protection • The loss of assimilative capacity for future industry or development • The loss of benefits associated with the current high water quality, such as fishing or tourism uses. The new or expanded action would be allowed to measurably reduce the water quality only if it is demonstrated that the action has selected the combination of site, technical and managerial approaches that will minimize the effect on water quality. Alternative approaches that must be evaluated include: • Pollution prevention or source control to reduce toxic compound discharges • Reuse or recycling of wastewater • Water conservation to minimize production of wastewater • Land application or infiltration to reduce surface water discharges • Alternative or enhanced treatment technologies • Improved operation and maintenance of existing facilities • Seasonal or controlled discharge to avoid critical water quality conditions • Water quality offsets with another water quality action (point or non-point source), providing no net decrease of water quality Tier III water bodies are specially designated as outstanding resource waters. The revised standards do not initially define Tier III water bodies; however, the standards allow the public or the Ecology to nominate water bodies for inclusion in the Tier III class. There are two classes within Tier III: Tier III(A) prohibits all future degradation, while Tier III(B) allows future degradation that does cause a “measurable change” to occur from well-controlled activities. Total Maximum Daily Load (TMDL) Studies Assimilative capacity is a term that describes the surface water’s ability to accept waste loadings without a permanent degradation of water quality. Ecology has conducted and completed waste load capacity studies, also known as Total Maximum Daily Load (TMDL) studies, for several major watersheds in the State of Washington. TMDL studies are used to determine the assimilative capacity of watersheds that are noted as “impaired” for having temperature or concentrations of a pollutant that are too high, such as BOD5; or potentially toxic pollutants, such as chlorine, ammonia, and metals. TMDL studies for dissolved oxygen have been conducted in the Snohomish River, impacting City of Marysville 4-13 Sewer Comprehensive Plan November 2011 CBOD, and ammonia effluent limitations for the major dischargers to the river system, including Marysville. Effluent limits for ammonia-N and CBOD were included in the 2005 permit based on Ecology’s findings in the Snohomish River Estuary TMDL study. The City’s WWTP discharges to Steamboat Slough, a branch of the Snohomish River, and therefore was included in the TMDL study. Table 4-3 summarizes the more stringent effluent limits that were placed on the City during its 2005 NPDES permit renewal. TABLE 4-3 City of Marysville 2005 NPDES/TMDL Seasonal Effluent Limits Parameter Average Month (lb/d) Maximum Day (lb/d) Ammonia-N 178 403 CBOD5 419 672 The limits shown in Table 4-3 apply to the low flow season from July through October. STATE ENVIRONMENTAL POLICY ACT The WAC 173-240-050 requires a statement in all wastewater comprehensive plans regarding proposed projects in compliance with the State Environmental Policy Act (SEPA), if applicable. The capital improvements proposed in this plan will fall under SEPA regulations. A SEPA checklist is included in Appendix I of this report for use in the environmental review for this NON-PROJECT action. In most cases a determination of non-significance is issued (DNS), however, if a project will have a probable significant adverse environmental impact an environmental impact statement (EIS) will be required. GROWTH MANAGEMENT Snohomish County’s GMA Comprehensive Plan establishes 13 sub-areas in which the county and cities within the sub-areas work together to set out urban growth areas (UGAs), policies for directing urban growth, and land use designations within urban and rural areas. The Marysville Comprehensive Plan includes land use policies and zoning designations that are consistent with the Snohomish County GMA Comprehensive Plan. Marysville City Council adopted a Comprehensive Land Use Plan on April 25, 2005, Ordinance #2569. 4-14 City of Marysville November 2011 Sewer Comprehensive Plan ACCREDITATION OF ENVIRONMENTAL LABORATORIES (WAC 173-050) The State of Washington recently established a requirement that all laboratories reporting data to comply with NPDES permits must be generated by an accredited laboratory. This accreditation program establishes specific tasks for quality control and quality assurance (QA/QC) that are intended to ensure the integrity of laboratory procedures. Accreditation requirements must be met for any on-site laboratory or outside laboratory used to analyze samples. Only accredited laboratories may be used for analyses reported for compliance with NPDES permits. In planning for an on-site laboratory, staffing must be sufficient to allow for QA/QC procedures to be performed. The City of Marysville’s laboratory is currently accredited to perform BOD, TSS, Dissolved Oxygen, PH, Total Residual Chlorine, and Fecal Coliform testing. MINIMAL STANDARDS FOR SOLID WASTE HANDLING (WAC 173-304) Grit and screenings are not subject to the sludge regulations in WAC 173-308, but its disposal is regulated under the State solid waste regulations, WAC 173-304. Waste placed in a municipal solid waste landfill must not contain free liquids, nor exhibit any of the criteria of a hazardous waste as defined by WAC 173-303. To be placed in a municipal solid waste landfill, grit and screenings must pass the paint filter test, which determines the amount of free liquids associated with the solids, and the toxic characteristics leachate procedure (TCLP) test, which determines if the waste has hazardous characteristics. WETLANDS Dredging and Filling Activities in Natural Wetlands (Section 404 of the Federal Water Pollution Control Act) A Corps permit is required when locating a structure, excavating, or discharging dredged or fill material in waters of the United States or transporting dredged material for the purpose of dumping it into ocean waters. Typical projects requiring these permits include the construction and maintenance of piers, wharves, dolphins, breakwaters, bulkheads, jetties, mooring buoys, and boat ramps. If wetland fill activities cannot be avoided, negative impacts can be mitigated by creating new wetland habitat in upland areas, and if other federal agencies agree, the Corps will generally issue a permit. Wetlands Executive Order 11990 This order directs federal agencies to minimize degradation of wetlands and enhance and protect the natural and beneficial values of wetlands. This could affect siting of pump stations and sewer lines. City of Marysville 4-15 Sewer Comprehensive Plan November 2011 SHORELINE MANAGEMENT ACT The Shoreline Management Act of 1971 (RCW 90.58) establishes a broad policy giving preference to shoreline uses that protect water quality and the natural environment, depend on proximity to the water, and preserve or enhance public access to the water. Shoreline Management Act jurisdiction extends to lakes or reservoirs of 20 acres or greater, streams with a mean annual flow of 20 cubic feet per second (CFS) or greater, marine waters, and an area inland 200 feet from the ordinary high water mark. Projects are reviewed by local governments according to state guidelines and a local Shoreline Master Program. Marysville’s wastewater treatment plant is located on the east side of Interstate 5 and the existing outfall is located within the shoreline of Steamboat Slough, a tributary of the Snohomish River. Due to the requirements imposed by the TMDL on the Snohomish River, the City constructed a new effluent transfer pipeline conveying effluent from the City of Marysville Wastewater Treatment Plant to the City of Everett Sewage Treatment Plant. The pipeline will enable the City of Marysville to divert effluent discharge during the summer months into the combined deep-water outfall in Port Gardner Bay, in order to meet summer water quality requirements for Steamboat Slough. During winter months, the water quality requirements for Steamboat Slough will be less stringent and the existing outfall can be used or flow could still be routed to Everett. FLOODPLAIN DEVELOPMENT PERMIT Local governments that are participating in the National Flood Insurance Program are required to review projects (including wastewater collection facilities) in a mapped flood plain and impose conditions to reduce potential flood damage from floodwater. A Floodplain Development Permit is required prior to construction. HYDRAULIC PROJECT APPROVAL Under the Washington State Hydraulic Code (WAC 220-110), the Washington State Department of Fish and Wildlife (WDFW) requires a hydraulic project approval (HPA) for activities that will “use, divert, obstruct, or change the natural flow or bed” of any waters of the state. For City activities such as pipeline crossings of streams, or WWTP outfall modifications, an HPA will be required, and will include provisions necessary to minimize project specific and cumulative impacts to fish. PRETREATMENT REQUIREMENTS Publicly owned treatment works are subject to local and national pretreatment standards. The federal standards are provided in 40 Code of Federal Register, Part 403. Chapter 14.20 of the Marysville Municipal Code sets pretreatment standards to prevent the introduction of pollutants in the collection system. Prohibited discharges could disrupt operations at the WWTP and potentially pass through the treatment process inadequately treated and discharge to receiving waters. Prohibited discharges, at a minimum, include 4-16 City of Marysville November 2011 Sewer Comprehensive Plan solids that could cause obstructions, high temperature wastes, petroleum wastes, radioactive materials, flammable/explosive waste, or oxygen demanding pollutants. In general, waste discharged to the sewer system is expected to contain characteristics similar to residential wastewater (i.e., pH, temperature, TSS, turbidity, color, BOD, chemical oxygen demand (COD), toxicity, or odor). The City’s pretreatment standards also control the introduction of fats, oils, and grease (FOG). ON-SITE SEPTIC SYSTEM REGULATIONS In some cases wastewater may be treated and disposed of on-site either by individual septic systems or community systems. On-site septic systems should be designed to meet the DOH design standards. Approval of the systems will be made either by the Snohomish Health District for systems under 3,500 gallons per day, or DOH for large on- site sewage systems (LOSS) less than 100,000 gallons per day but greater than 3,500 gallons per day as per RCW 70.118B and WAC 246-272B, or Ecology for systems that are over 100,000 gallons per day in capacity. The State Board of Health statute that provides the authority for the DOH to adopt rules for sewage is found in RCW 43.20. It is the City’s policy that all future development within the UGA connects to the sewer system instead of installing individual septic systems. The City is planning for service to all areas within its sewer boundary whether or not the area is currently sewered. Service to areas currently on septic SEWER ORDINANCES AND PLANNING POLICIES The Marysville Municipal Code Title 14 sets rules and regulations for the City’s water and sewer systems. The sections of this code relevant to this Plan are listed in Table 4-5 and provided in Appendix B. MMC 14.01.050 Sewer connection required, requires structures within its service area 200 feet from available utilities to connect to the sewer system. (Note: Homes and businesses within the City’s UGA in Snohomish County jurisdiction are usually served by septic systems.) MMC 14.05.020 Discharge restriction into sanitary sewers, prohibits the discharge of unsuitable materials or stormwater into the sewer system. Chapter 14.07 MMC Fees, Charges and Reimbursements, establishes water and sewer rates for customers inside and outside the City limits. Chapter 14.03 MMC Rules for Construction, Installation and Connection, sets rules for construction standards and Chapter 14.20 MMC Wastewater Pretreatment, sets the requirements for wastewater pretreatment. Chapter 14.05 MMC Rules for Customers – Payment and Collection of Accounts provides additional information on sewer rates, connection charges, utility bills, and disconnection and reconnection service and charges. The siting of any wastewater facilities, such as pump stations or wastewater treatment plant, must adhere to the City’s Comprehensive Plan and Unified Development Codes at the time of construction. City of Marysville 4-17 Sewer Comprehensive Plan November 2011 TABLE 4-4 Title 14 MMC Water and Sewers Chapter Title 14.01 General Provisions 14.03 Rules for Construction, Installation, and Connection 14.05 Rules for Customers-Payment and Collection of Accounts. 14.07 Fees, Charges, and Reimbursements 14.09 Water and Sewer Conservation Measures 14.20 Wastewater Pretreatment 14.32 Utility Service Area CITY WASTEWATER OPERATION AND MAINTENANCE STANDARDS Chapter 14.03 MMC sets forth the wastewater requirements for construction, installation and connection. All wastewater facilities must meet Washington State Department of Ecology design standards as delineated in Criteria for Sewage Works Design (Orange Book). The code also includes appropriate reference to the Uniform Plumbing Code. The City’s Sanitary Sewer Design Standards were last revised in May 2007. City of Marysville 5-1 Sewer Comprehensive Plan November 2011 CHAPTER 5 EXISTING FACILITIES INTRODUCTION This Chapter describes existing facilities that are relevant to the City of Marysville’s wastewater collection and treatment systems. The facilities include the wastewater collection system, pump stations and force mains, wastewater treatment and disposal facilities. This Chapter also describes interlocal agreements the City has with local jurisdictions. WASTEWATER COLLECTION SYSTEM PRESSURE AND GRAVITY SEWERS The City’s collection system is organized around eight trunk sewer systems: A, B, C, D, F, F-A, G and the Lakewood Trunk. Each trunk sewer is listed in Table 5-1 along with the approximate area of the existing service area. The potential service area for each trunk sewer is also shown on Figure 5-1. All components of the collection system discharge to the treatment facility either through Trunk A or Trunk C. TABLE 5-1 Trunk Sewer Service Area Trunk Sewer ID Service Area (Acres)(1) A 3,341 B 307 C (East and West) 3,267 D 4,054 F 1,447 F-A 301 G 965 Lakewood 901 (1) Trunk area within UGA The general direction of flow in the City’s collection system is from north to south, starting near Arlington and discharging to the wastewater treatment facility at the south end of the service area. Most of the service area is served by gravity sewers. The City operates and maintains 15 pump stations; over half of these stations serve small developments, while the rest serve significant portions of the sewer service area. SR 9I-5 84TH ST NE SR 531 STATE AVESR 52951ST AVE NE99TH AV NEGROVE STSMOKEY POINT BLVD88TH ST NE 108TH ST NE 152ND ST NE 83RD AVE NE47TH AVE NECEDAR AVE4TH ST 140TH ST NE 8TH ST FO R T Y - F I V E R D 34TH AVE NESOPER HILL RD 136TH ST NE 44TH ST NE 132ND ST NE 71ST AVE NE79TH AVE NE80TH ST NE 188TH ST NE 48TH DR NE47TH AV NE27TH AVE NE64TH ST NE 116TH ST NE SHOULTES RD76TH ST NE 52NDST NE GROVE ST 100TH ST NE 84TH ST NE SR 531 132ND ST NE 51ST AVE NESUNNYSIDE BLVDSR 967TH AVE NE51ST AVE NESTATE AVEI-5I-5SR 9 2ND ST 172ND ST NE172ND ST NE 67TH AVE NETRUNK A TRUNK G F TO A INTERTIE TRUNK C TRUNK C TRUNK F TRUNK D LAKEWOOD TRUNK TRUNK A TRUNK B 122ND ST EAGLE BAY SUNNYSIDE ASHAVENUE SOPER HILL REGAN ROAD 3RD STREET 51ST AVENUE LAKEWOOD SD 88TH STREET KELLOGG RIDGE QUIL CEDA GLEN CARROLL'S CREEK MARYSVILLE WEST TREATMENT LAGOON WATERFRONT PARK CEDAR CREST VISTA QUILCEDA ELEMENTARY MOUNTAIN VIEW SHORES COUGARCREEKELEMENTARY 31ST AVE INDUSTRIAL PARK SMOKEY POINT MOBILE ESTATES Trunk Lines F To A Intertie Lakewood Trunk Trunk A Trunk B Trunk C Trunk D Trunk F Trunk G Collection Sewers Force Mains Marysville Private Lift Stations Marysville Private Trunk Basins Basin A Basin B Basin C East Basin C West Basin D Basin F Basin F-A Intertie Basin G Lakewood Basin Sewer Comprehensive Plan Figure 5-1 Collection System 0 1 20.5 Miles 5-2 City of Marysville November 2011 Sewer Comprehensive Plan The trunk sewer serving the largest portion of the sewer service area population is Trunk A. Trunk A is located in the middle of the sewer service area and extends the full length of the current urban growth area. Along this alignment, other trunk tributary areas discharge into Trunk A. Trunk F discharges to Trunk A upstream of the 51st Avenue Pump Station. Trunk A discharges to the 51st Pump Station and flow continues south through a 36-inch gravity pipeline. Trunk C (east) discharges to Trunk A at 88th Street. Trunk B discharges to Trunk A at 72nd Street NE. Trunk D connects to Trunk A near 47th Avenue and 1st Street. Trunk A discharges to the headworks of the WWTP. Only Trunk G and Trunk C (west) are not a directl tributary to Trunk A. Trunk G serves part of the Tulalip Tribe west of Interstate 5 and connects to Trunk C (west) through the Marysville West Pump Station. Trunk C (west) discharges to the West Trunk Pump Station which then discharges to the headworks of the wastewater treatment plant. The City’s collection system includes 210 miles of gravity sewer ranging from 6- to 48-inch diameter pipe, force main ranging from 2- to 12-inch diameter pipe, and 15 pump stations. As of December 2010, the collection system had a total of 15,963 connections. Of this total, approximately 15,103 were residential connections, and 860 were schools, commercial and industrial connections. Table 5-2 provides an inventory of the gravity sewer lines by length, pipe diameter, and material for all pipe diameters 6-inches and greater. This inventory is based on GIS information compiled by City staff. Approximately two-thirds of the City’s sewer system is constructed with PVC pipe. Table 5-3 provides a similar inventory of the force main pipe. The table includes the force main associated with the City of Everett outfall as well as force main piping for each individual pump station. PUMP STATIONS An inventory of the City’s sewage pump stations is presented in Table 5-4. The pump stations with the highest capacities are the Soper Hill Pump Station, Sunnyside Pump Station, 51st Avenue Pump Station, Marysville West Pump Station and the West Trunk Pump Station. The location of each of the City’s pump station is shown on Figure 5-1. Privately owned pump stations are not listed in Table 5-4. Table 5-4 also presents information regarding the year installed, trunk sewer service area, auxiliary power, and other features for each pump station. Additional details are included in Appendix C. City of Marysville 5-3 Sewer Comprehensive Plan November 2011 TABLE 5-2 Gravity Sewer Inventory Diameter (inches): Unknown < 6 6 7 - 8 10 12 14 15 16 - 18 20 - 21 24 30 36 42 48 Total (ft.) Asbestos Cement 5,616 252 5,197 11,064 Cast Iron 188 296 484 Clay 462 4,256 475 432 474 6,099 Concrete 140 1,414 59,820 9,149 9,095 284 8,506 27,124 13,102 6,704 5,734 7,845 9,375 7,537 165,829 Ductile Iron 38 3,984 1,052 1,526 873 1,163 773 9,407 HDPE 1,773 915 1,022 80 51 3,842 PVC 1,686 539 11,763 573,150 103,798 67,865 22,505 18,967 4,277 5,602 9,588 819,740 PVC Perforated 294 294 Reinforced Concrete Pipe 1,325 136 213 70 1,744 Unknown 13,843 47 7,788 42,286 4,545 6,124 53 2,863 8,062 1,784 2,524 2,119 249 546 92,831 Total (ft.) 15,708 586 21,908 691,180 121,510 85,633 5,534 33,874 55,242 19,646 15,992 18,426 7,915 9,624 8,556 1,111,334 Total (%) 1.41% 0.05% 1.97% 62.19% 10.93% 7.71% 0.50% 3.05% 4.97% 1.77% 1.44% 1.66% 0.71% 0.87% 0.77% 100.00% Total (Miles) 3.0 0.1 4.1 130.9 23.0 16.2 1.0 6.4 10.5 3.7 3.0 3.5 1.5 1.8 1.6 210.5 5-4 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 5-3 Inventory of Force Main Pump Station Length (feet) Diameter (inches) Material Soper Hill 4,295 10 DI Carrol’s Creek 3,820 6 DI 88th Street 4,464 10 DI Regan Road 25 4 DI 3rd Street 35 8 DI Marysville West 1,928 14 CI Cedar Crest Vista 1,188 4 DI 51st Avenue 352 20 HDPE Sunnyside 461 12 DI Kellogg Ridge 1,692 4 DI Quilceda Glen 147 4 DI Ash Avenue 63 4 DI West Trunk 2,325 16 DI Eagle Bay 628 4 DI Waterfront Park 618 2.5 PVC Total: Pump Stations 22,041 City of Everett(1) Effluent Discharge 4,700 16,000 36 26 HDPE HDPE (1) One 36-inch boring (4,700 feet total) and two parallel 26-inch-diameter pipes. City of Marysville 5-5 Sewer Comprehensive Plan November 2011 TABLE 5-4 Inventory Of Sewage Pump Stations ID Year Online Trunk Sewer System Station Type Pump Manufacturer/Model No. of Pump Capacity (gpm) TDH (ft) Motor (hp) Standby Power/Capacity (kW) Telemetry Other Soper Hill Pump Station(1) 2003 D Submersible Pre-rotation Wemco F4K-S-F-E5B5 2 550 1250 83 115 20.9 60 Yes 3 Phase 175KW Yes Two speed motors Carroll’s Creek Pump Station 2002 (2004 upgrade) F Submersible Pre-rotation Wemco S4PX750FC 2 400 40 7.5 No Yes Portable Generator 88th Street Pump Station 1999 (2009 upgrade) C Submersible Flygt/3127.090 2 500 38 10 Yes 3 Phase 90KW Yes Control Panel Upgrade in 2009 Regan Road Pump Station 1983 (2007 upgrade) A Submersible Pre-rotation Wemco D4K-HS-DKXA6 2 120 22 4.1 Yes 3 Phase 25KW Yes Portable Generator Marysville West Pump Station 1968 G Wet Well/Dry Pit Fairbank Morse/541 3B28 2 1,150 Unkown 10 No Yes Portable Generator Cedar Crest Vista Pump Station 1996 (2008 upgrade) D Submersible Pre-rotation Wemco D3K-5-DKXA4 2 450 Unkown 7.5 No Yes Portable Generator 51st Avenue Pump Station(2) 1969 (2004 upgrade) A Submersible Pre-rotation Wemco/F10K-SS-870 3 800 30 10 Yes 3 Phase 180KW Yes Two speed motors Wemco/F10K-SS-1160 3 3,250 23 30 Sunnyside Pump Station 2000 (2010 upgrade) D Wet Well/Dry Pit Wemco/E5K-EEXR4 3 890 53.3 20 Yes 3 Phase 150KW Yes Third pump upsized in 2010 3rd Street Pump Station(3) 1997 D Submersible Flygt/3085.092-6011 2 200 18 3 No Yes Portable Generator 5-6 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 5-4 - (continued) Inventory Of Sewage Pump Stations ID Year Online Trunk Sewer System Station Type Pump Manufacturer/Model No. of Pump Capacity (gpm) TDH (ft) Motor (hp) Standby Power/Capacity (kW) Telemetry Other Kellogg Ridge Pump Station(4) 2003 A Submersible Hydromatic S4PX 2 400 66 10 No Yes Portable Generator Quilceda Glen Pump Station(4) 2003 A Submersible Hydromatic S4NX 2 250 14 2 No Yes Portable Generator Ash Avenue Pump Station 2004 C Submersible Pumpex 2 200 Unkown 3 No Yes Portable Generator West Trunk Pump Station 1994 C Dry Pit/Wet Pit Wemco F10K-SS 3 3,300 22 25 Yes 125 kW 3 Ph Yes Eagle Bay Pump Station 2009 D Submersible Non-Clog Hydromatic H4H-H4HX-1500JC 2 850 Unknown 15.6 No Yes Portable Generator Waterfront Park Pump Station 2005 C Submersible Grinder Hydromatic HPG-FHX-300JC 2 57 Unknown 3 No No Portable Generator (1) The 2 pumps at the Soper Hill Lift Station are set for 1,160 and 1,750 rpm’s. At the lower speed, pump capacity is 550 gpm; at the higher speed, capacity is 1,250 gpm. (2) The 3 pumps at the 51st Street Lift Station are set for 870 and 1,160 rpm’s. At the lower speed, capacity for each pump is 800 gpm at the higher speed each pump has a capacity of 3,250 gpm. (3) The 3rd Street Lift Station capacity is estimated from pump curve information. (4) Pump capacity estimated from pump model and standard pump curve for horsepower rating. City of Marysville 5-7 Sewer Comprehensive Plan November 2011 WASTEWATER TREATMENT PLANT The existing lagoon wastewater treatment plant (WWTP) is in the southwest corner of the City on Ebey Slough. The WWTP was originally constructed at the current site in 1959. After a plant expansion in 1980-1981, the biological treatment train consisted of two lagoons, each divided with curtains into two treatment cells. The first three cells in the train were partially mixed and aerated with aspirating-type aerators, while the fourth cell served as a stabilizing pond. In addition to the lagoons, the WWTP included influent and effluent flow monitoring flumes, manually cleaned bar screens, a grit chamber, and a chlorine contact chamber using gaseous chlorine. Another plant expansion occurred in 1994. A portion of the north lagoon system was converted to two complete mix aerated lagoon cells. Influent screw pumps and mechanically cleaned bar screens were added to the headworks. A third channel was constructed in the headworks to accommodate a future screw pump. Effluent sand filters (manufactured by Dynasand) were added to remove solids from the lagoon effluent, and a new chlorine contact tank was constructed. In 2004 another upgrade of the wastewater treatment plant was completed in two phases. Phase 1 of the upgrade included the addition of 2 new complete mix aerated lagoon cells, one new influent screw pump, one new influent bar screen, and 4 effluent pumps. Phase 2 of the upgrade included the addition of 2 more complete mix aerated lagoon cells, 1,600 square feet of effluent sand filters (manufactured by Dynasand), UV disinfection, and an effluent pipeline to the City of Everett. The WWTP biological treatment components include six complete mix aerated lagoon cells, three partially mixed facultative lagoons, and a facultative only stabilization lagoon. The plant discharges to Steamboat Slough in the Snohomish River Estuary (designated as a Class A Marine receiving water in the vicinity of the outfall) during high river flow months (November through June). The plant discharges to the City of Everett’s South Everett Pump Station (SEPS) in route to the Deep Marine Outfall in Puget Sound, during low river flow periods (July through October). WWTF DESIGN CRITERIA AND CURRENT PLANT LOADINGS The design criteria for the Marysville WWTP, as presented in the drawings for Phase 2 of the WWTP Upgrade and Expansion (Tetratech/KCM, 2003) are shown in Table 5-5. Phase 2 was completed at the end of 2004. 5-8 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 5-5 Wastewater Treatment Plant Design Flows and Loading(1) Parameter Phase 1 Phase 2 Design Year 2004 2010 Flows (mgd) Average Annual 8.52 10.1 Maximum Month 10.7 12.7 Maximum Day 13.1 15.6 Peak Hour 17.2 20.3 Mass Loading (lb/day) Annual Average BOD5 14,943 17,070 TSS 14,943 17,815 Average Day, Max. Month BOD5 17,632 20,143 TSS 20,322 24,229 Maximum Day BOD5 21,816 24,922 TSS 31,977 38,125 (1) This information is from the design drawings prepared by Tetratech/KCM, Phase 2 (2003). NPDES Permit The City’s most recent NPDES permit was issued by the Department of Ecology on July 1, 2005 and expired on June 30, 2010. The City submitted an application for NPDES renewal in December 2009. As of the writing of this document, the City has not received their new NPDES permit. It is expected that they will receive the new permit sometime in late 2011 to early 2012. Due to the outcome of the past TMDL Study on the Snohomish River, the WWTP has different NPDES permit limits for the low river flow period (July through October) than the high river flow period (November through June). The permit issued in 2005 included new limits for the low flow period. These new limits are summarized in Tables 5-6 and 5-7. City of Marysville 5-9 Sewer Comprehensive Plan November 2011 TABLE 5-6 Wastewater Treatment Plant NPDES Permit Limits Low Flow Season (July – October) NPDES Effluent Limitations Average Monthly Average Weekly CBOD5 25 mg/L(1) 40 mg/L TSS 30 mg/L(1) (3,180 lb/d) 45 mg/L (4,770 lb/d) pH 6.0 - 9.0 (daily) Fecal Coliform 200 cfu / 100mL 400 cfu / 100mL NPDES Effluent Limitations Average Monthly Maximum Daily Ammonia (as N) 178 lb/d 403 lb/d CBOD5 419 lb/d 672 lb/d (1) Or 15 percent of the respective monthly average influent concentrations, whichever is more stringent TABLE 5-7 Wastewater Treatment Plant NPDES Permit Limits High Flow Season (November through June) NPDES Effluent Limitations Average Monthly Average Weekly CBOD5 25 mg/L(1) (2,650 lb/d) 40 mg/L (4,240 lb/d) TSS 30 mg/L(1) (3,180 lb/d) 45 mg/L (4,770 lb/d) PH 6.0-9.0 (daily) Fecal Coliform 200 cfu / 100mL 400 cfu / 100mL (1) Or 15 percent of the respective monthly average influent concentrations, whichever is more stringent Table 5-8 summarizes the WWTP NPDES Permit Facility Loading Criteria. TABLE 5-8 Wastewater Treatment Plant NPDES Permit Facility Loading Criteria(1) Parameter Value Average Flow for the Maximum Month 12.7 MGD Influent BOD5 Loading for Maximum Month 20,143 lbs/day Influent TSS Loading for the Maximum Month 24,229 lbs/day (1) Current NPDES limits through 2010 (Appendix A). 5-10 City of Marysville November 2011 Sewer Comprehensive Plan The 2004 WWTP Phase 1 and Phase 2 upgrades included: • Installation of an additional influent screw pump. • Construction of four new complete mix aerated lagoon cells. • The addition of 20 high-speed surface aerators and 16 surface aspirating aerators in complete mix lagoon cells 2A, 2B, 3A, and 3B; • Modification and expansion of continuous backwash, upflow sand filters, with construction of an additional 1600 square feet; • Installation of a low-pressure-high-intensity UV disinfection system in the renovated North Chlorine Contact Basin; • Installation of a supplemental hypochlorite disinfection storage and delivery system; • Installation of four 200 horsepower vertical turbine effluent pumps. • Construction and installation of a new effluent discharge pipeline to the City of Everett. • Modifications and renovations to the existing plant control/laboratory building; • Construction of a new maintenance building; • Associated site civil, electrical, instrumentation and control facilities. WWTP DESCRIPTION Figure 5-2 shows the site layout for the WWTP. The WWTP liquid stream treatment processes include influent screening, biological treatment and sludge settling in the complete mix cells, partially mixed and unmixed lagoon cells, coagulation, filtration, and ultraviolet disinfection. Headworks Incoming raw wastewater entering the WWTP from Trunk A is pumped with three Archimedes screw pumps to the level of the headworks. The force main from the West Trunk Pump Station discharges into the headworks upstream of the bar screens but downstream of the influent screw pumps. City of Marysville 5-11 Sewer Comprehensive Plan November 2011 The incoming wastewater is screened at the headworks to remove large solids. The headworks includes two mechanically cleaned screens (front-raked climber type, manufactured by John Meunier, Inc., of Quebec) and a manual screen in a bypass channel. The mechanically cleaned screens have a 1 ½ inch bar spacing. Influent Flow Measurement Influent flow is measured with a Parshall flume with a 30-inch throat width. Lagoon System Biological treatment of the wastewater is provided in the lagoon system. Design criteria for the lagoon system are summarized in Table 5-9. Following completion of the Phase 2 upgrades, the lagoon system consists of six complete mix aerated lagoons with mechanical surface and floating aerators, three partially mixed oxidation ponds and one unmixed stabilization pond. TABLE 5-9 Lagoon System Design Criteria Parameter Value Complete Mix Lagoons Number 6 Depth, feet 6.2 Volume, each, Million gallons 4.89 Total Area, Acres 14.5 Hydraulic Residence Time at Maximum Month Flow, Days, total 2.3 Number of Aspirating Aerators 24 Horsepower (each) 15 Number of High Speed Surface Aerators 30 Horsepower (each) 15 Oxidation Ponds Number 4 Depth, feet 6.2 Volume, total, Million gallons 116 Total Area, Acres 52.5 Hydraulic Residence Time at Maximum Month Flow, Days, total 9.0 Number of Aspirating Aerators 5 Horsepower (each) 7.5 5-12 City of Marysville November 2011 Sewer Comprehensive Plan Coagulation and Filtration Facilities Effluent sand filters enable the WWTP to meet NPDES permit requirements for effluent TSS (30 mg/L monthly average – 45 mg/L weekly average). Particularly in the spring and summer, the lagoons generate significant blooms of algae that must be removed with the filtration system. The filtration system is an upflow continuous backwash, monomedia type (Parkson Dynasand). The size of the filtration system was tripled during 2004 Phase 2 upgrades to 2,400 square feet of filter surface area from the previous 800 square feet. Alum (at a design dosage of 100 mg/L) is used for coagulation. Ultraviolet Disinfection System The WWTP had historically used gaseous chlorine for disinfection, prior to the 2004 upgrades. An Ultraviolet Light (UV) Disinfection System, manufactured by Infilco Degremont, Inc. (IDI, formerly Ondeo Degremont) was constructed and installed in the north chlorine contact tank for the design flow of 12.7 mgd. Each channel contains six Aquaray 40 units, each with 40 low pressure-high intensity lamps. There are a total of 480 lamps. The UV system increases its dose with an increase in flow and a reduction in transmittance. The IDI’s standard system was installed, with vertically oriented lamps arrayed perpendicular to flow. An additional channel was constructed for future growth. The UV system was designed for a minimum dose of 35,000 microwatt-sec/cm2. The design transmittance is 60 percent for filtered flow and 25 percent for unfiltered flow. A sodium hypochlorite system, a backup method for disinfection, was also constructed. The system utilizes the existing south chlorine contact tank, and was designed for 25 minutes contact time at year 2010 average annual flow and 20 minutes contact time at year 2010 maximum month flow. Effluent Pumps In Phase 1 of the 2004 upgrades, four new vertical turbine pumps were installed. The capacity of each of the 200 horsepower pumps is 4,700 gpm at a total dynamic head of 104 feet. The total capacity of the pumps, with one pump out of service, is 20.4 MGD. Effluent Disposal A new effluent pipeline was constructed in Phase 2 of the 2004 upgrades. In the summer low-river flow months (July through October), the WWTP conveys effluent through this pipeline to the City of Everett, and to the Deep Marine Outfall in Puget Sound. This second outfall allows the City to meet TMDL limits established for Steamboat Slough during low-river flow months. Effluent is conveyed through a 36-inch pipe across the Ebey, Steamboat, and Union Sloughs and then through twin 26-inch pipes to the City of Everett’s South End Pump Station (SEPS). From there it is discharged to the outfall in City of Marysville 5-13 Sewer Comprehensive Plan November 2011 Puget Sound. Effluent flow is measured through a 30-inch magnetic flow meter located at Marysville’s WWTP. During the balance of the year, effluent is discharged through the existing 28-inch pipeline to the outfall in Steamboat Slough. Effluent flow is measured with a 20-inch magnetic flow meter located at Marysville’s WWTP. INTERLOCAL AGREEMENTS The City of Marysville has updated or established service agreements with the City of Arlington, Snohomish County, Tulalip Tribes, Lake Stevens Sewer District, and the City of Everett. Some of these agreements cover items such as roads, fire and police service in addition to policies relating to sewer service. Each of these agreements is discussed below regarding land use and sewer planning considerations. In addition, the areas covered by these agreements are presented in Figure 5-3. CITY OF ARLINGTON In October 1996, the City completed an agreement with the City of Arlington titled Annexation and Service Area Settlement Agreement. This agreement established separate UGAs for each city which were approved by Snohomish County. Among other provisions of this agreement were that Marysville would continue to provide sewer service for the Smokey Point area that is within Arlington’s UGA and that Arlington would proceed with purchasing water and sewer facilities owned by Marysville that serve the Island Crossing area of Arlington. This part of the 1996 agreement has been completed, and Marysville no longer serves Island Crossing. Other parts of this agreement state that the two cities will coordinate land use planning for areas east of 67th Avenue SE, north of the Lakewood area and in the vicinity of the Arlington Airport. A copy of this agreement is included in Appendix B. SNOHOMISH COUNTY In June 1999, the City and Snohomish County completed an agreement titled Interlocal Agreement between the City of Marysville and Snohomish County Concerning Annexation and Urban Development within the Marysville Urban Growth Area. The primary purpose of this agreement was to identify areas within Snohomish County which the City may annex in the future. Under this agreement, both the City and County recognize the need to coordinate land use densities and designations and to facilitate an orderly transition of services and capital project at the time of annexation. Of specific importance for sewer planning is the need to reconcile land use densities between the City and County. The City requires a minimum of four dwelling units per acre in its UGA while the County may allow lower densities in its unincorporated areas. A copy of this agreement is included in Appendix B. 5-14 City of Marysville November 2011 Sewer Comprehensive Plan TULALIP TRIBES In December 1998, the City of Marysville and the Tulalip Tribes executed a Memorandum of Understanding regarding sanitary sewer and water service for a portion of the Tulalip Business Park. For sewer service, this agreement would allow up to 150,000 gpd with a peak flow of 150 gpm. The agreement allow for average strength waste of 201 – 300 mg/L BOD5. the Tribe’s point of connection is located at 90th Street and 35th Avenue in the vicinity of the 88th Street Pump Station. Flow from the Tulalip Business Park will be subject to the City’s Pretreatment Resolution and installation of a master meter and flow monitoring station. A copy of this agreement is included in Appendix B. As of 2004, it was not expected that the Tulalip Tribes would utilize this capacity due to construction of its own membrane bioreactor (MBR) treatment plant. LAKE STEVENS SEWER DISTRICT In April 1999, the City and the Lake Stevens Sewer District entered into a Sewerage Disposal Agreement to address sewer service in a “overlap” area shown on Figure 5-3. This area is located southeast of the City between State Highway 9 to the east, 83rd Street to the west, Soper Hill Road to the south, and 44th Street to the north. This area is currently only partly sewered, but the City has recently completed the Soper Hill Pump Station and a 12-inch gravity pipeline along this road. The Plat of Ridgewood is sewered, and under this agreement the District will continue to own and operate this sewer system. The intent of this agreement is for both the City and District to cooperate for providing sewer service to other parts of the “overlap” area. In addition to the Sewage Disposal Agreement, the City passed Ordinance No. 2284 establishing a satellite sewer rate classification for the “overlap.” For this area, the City shall charge the same sewer rate as the District’s plus an administrative fee of 15 percent. Copies of both agreements are included in Appendix B. CITY OF EVERETT In March 2002, the City of Marysville and the City of Everett entered into an agreement for Conveyance and Discharge of Treated Wastewater. Under this agreement the City of Marysville has the ability to pump, convey and discharge up to 20 mgd (peak flow) of effluent to Everett’s Port Gardner Bay marine outfall. Under the terms of this agreement, the City of Marysville agreed to pay 33.3 percent for design, permitting and construction of new facilities, $499,500 for its portion for existing facilities, and 15 percent of the amounts in the first two parts plus 33 percent of any interest costs. Marysville would also City of Marysville 5-15 Sewer Comprehensive Plan November 2011 be responsible for 100 percent of the cost for its own pumping and conveyance facilities and agreed to its proportionate share of operation and maintenance costs. Following the Agreement for Conveyance and Discharge of Treatment Wastewater, the City of Marysville and the City of Everett also entered into an Agreement for Operation of the South Effluent Pump Station (SEPS). This agreement establishes the terms and conditions under which Everett shall operate and maintain the SEPS. Among the provisions are ones where Everett will notify Marysville of flow, chlorine levels, scheduled maintenance requirements, and emergency operations. In turn, Marysville shall notify Everett of changed conditions in the quantity of its effluent, scheduled maintenance requiring termination flows, and emergency operation. Copies of both agreements are included in Appendix B. MUTUAL AID AGREEMENT Marysville is party to a 2006 “Sewer and Water Mutual Aid Agreement” that addresses sharing of personnel and equipment during emergency conditions. Such mutual aid is authorized in State law, at Chapter 39.34 RCW. Other parties to the agreement include the Cities of Edmonds, Everett, Lynnwood, Monroe, Arlington and Snohomish: and the following special districts: Alderwood, Mukilteo, Olympic View and Silver Lake Water and Sewer Districts. A copy of this agreement is included in Appendix B. 16THAVE NW132ND ST NE 99TH AVE NESR 52834TH AVE NE79TH AVE NE71ST AVE NESR 92 76TH ST NE 84TH ST NE SR 980TH ST NE ASH AVE116TH ST NE SR 984TH ST NE 52NDST NESHOULTES RD132ND ST NE 108TH ST NE SR 531 67TH AVE NE SMOKEY POINT BLVDI -5 I-551ST AVE NE88TH ST NE 67TH AVE NE 51ST AVE NE I-523RDAVE NEARMARRD140TH ST NE 48TH DR NE136TH ST NE FORTY-FIVE RD3RD AVE NE44TH ST NESUNN YSIDE BLVDSR 52927TH AVE NECEDAR AVE4TH ST47TH AVE NE100TH ST NE51ST AVE NEMARINE DR152ND ST NE 83RD AVE NEGROVE ST 64TH ST NE 172ND ST NE STATE AVE67TH AVE NESR 9I-5 E L AKE GOODWIN RDLAKEWO O D RD SR 53 1140TH ST NE M A RIN E D R City of Arlington Tulalip Reservation City of Everett Tulalip Business Park (inactive) Everett Effluent Transfer Arlington Interlocal Agreement SewerComprehensivePlan Fig 5-3 Interlocal Agreements 0 1 20.5 Miles Sewer service area Future planning areas City limits 5-16 City of Marysville November 2011 Sewer Comprehensive Plan REFERENCES 1. Comprehensive Sanitary Sewerage Plan, City of Marysville , HCWL, October 1990 2. Comprehensive Sanitary Sewerage Plan, City of Marysville , HCWL, KCM, Jones and Stokes, June 1997 3. Sanitary Sewer Infiltration/Inflow Analysis, HCWL, September, 1999 4. Wastewater Treatment Plant Capital Facilities Plan, Final, February, 2001, KCM 5. Wastewater Treatment Plant Upgrade and Expansion –Phase 1, Volume 2 and Phase 2, Volume 2 Drawings, KCM, 2002 City of Marysville 6-1 Sewer Comprehensive Plan November 2011 CHAPTER 6 EXISTING AND PROJECTED WASTEWATER FLOWS AND CHARACTERISTICS INTRODUCTION Adequate design of wastewater treatment and conveyance facilities requires the determination of the quantity and quality of wastewater generated from each of the contributing sources. Typically, wastewater is predominantly domestic in origin with lesser amounts contributed by commercial and industrial businesses and by public use facilities such as schools, parks, hospitals, and municipal functions. Infiltration and inflow (I/I) contributions result from groundwater and surface water entering the sewer system during periods of high groundwater levels and rainfall, respectively. DEFINITION OF TERMS In this Chapter, the existing wastewater characteristics for the service area are analyzed and projections made for future conditions. The terms and abbreviations used in the analysis are described below. WASTEWATER Wastewater is water-carried waste from residential, business and public use facilities, together with quantities of groundwater and surface water which enter the sewer system through defective piping and direct surface water inlets. The total wastewater flow is quantitatively expressed in millions of gallons per day (mgd). DOMESTIC WASTEWATER Domestic Wastewater is wastewater generated from single and multifamily residences, permanent mobile home courts, and group housing facilities such as nursing homes. Domestic wastewater flow is generally expressed as a unit flow based on the average contribution from each person per day. The unit quantity is expressed in terms of gallons per capita per day (gpcd). EQUIVALENT RESIDENTIAL UNIT (ERU) An Equivalent Residential Unit (ERU) is a baseline wastewater generator that represents the average single family residential household. An ERU can also express the average annual flow contributed by a single-family household, in units of gallons per day, or an annual average loading (of 5-day biochemical oxygen demand or total suspended solids) contributed by a single-family household, in units of pounds per day. 6-2 City of Marysville November 2011 Sewer Comprehensive Plan NON-RESIDENTIAL WASTEWATER Non-residential Wastewater is wastewater generated from business activities, such as restaurants, retail and wholesale stores, service stations, and office buildings. Non- residential wastewater quantities are expressed in this Plan in terms of equivalent residential units (ERUs). INFILTRATION Infiltration is groundwater entering a sewer system by means of defective pipes, pipe joints or manhole walls. Infiltration quantities exhibit seasonal variation in response to groundwater levels. Storm events or irrigation trigger a rise in the groundwater levels and increase infiltration. The greatest infiltration is observed following significant storm events prolonged periods of precipitation. Since infiltration is related to the total amount of piping and appurtenances in the ground and not to any specific water use component, it is generally expressed in terms of the total land area being served. The unit quantity generally used is gallons per acre per day. INFLOW Inflow is surface water entering the sewer system from yard, roof and footing drains, from cross connections with storm drains and through holes in manhole covers. Peak inflow occurs during heavy storm events when storm sewer systems are taxed beyond their capacity, resulting in hydraulic backups and local ponding. Inflow, like infiltration, can be expressed in terms of gallons per capita day or gallons per acre per day. WWTP flow records are utilized to characterize combined infiltration and inflow in the Marysville system in terms of peak hour, peak day, maximum month, and average annual I/I. AVERAGE DRY WEATHER FLOW Average Dry Weather Flow is wastewater flow during periods when the groundwater table is low and precipitation is at its lowest of the year. The dry weather flow period in western Washington normally occurs during July through October. During this time, the wastewater strength is highest, due to the lack of dilution with the ground and surface water components of infiltration and inflow. The higher strength coupled with higher temperatures and longer detention times in the sewer system create the greatest potential for system odors during this time. The average dry weather flow is the average daily flow during the three lowest consecutive flow months of the year. City of Marysville 6-3 Sewer Comprehensive Plan November 2011 AVERAGE ANNUAL FLOW Average Annual Flow is the average daily flow over a calendar year. This flow parameter is used to estimate annual operation and maintenance costs for treatment and pump station facilities. MAXIMUM MONTH FLOW (TREATMENT DESIGN FLOW) Maximum Month Flow is the highest monthly flow during a calendar year. In western Washington, the maximum month flow occurs in the winter due to the presence of more I/I. This wintertime flow is composed of the normal domestic, commercial and public use flows with significant contributions from inflow and infiltration. The predicted maximum month flow at the end of the design period is used as the design flow for sizing treatment processes and selecting treatment equipment. PEAK HOUR FLOW Peak Hour Flow is the highest hourly flow during a calendar year. The peak hour flow in western Washington usually occurs in response to a significant storm event preceded by prolonged periods of rainfall, which have previously developed a high groundwater table in the service area. Peak hour flows are used in sizing the hydraulic capacity of wastewater collection, treatment and pumping components. Peak hour flow is typically determined from treatment plant flow records and used to estimate future flows. However, in this analysis there is concern that the WWTP flow meters may not be reading accurately at peak hour flows. Without accurate data for peak hour flows, the recommended approach is to calculate a flow based on accepted criteria. Ecology’s Orange Book provides a method shown in its Figure C1-1 based on a ratio of peak hourly flow to design average flow as presented below: Q peak hourly = 18 + square root (P) where: Q design average 4 + square root (P) Q peak hourly = Maximum rate of wastewater flow Q design average = Design average, or average annual, recorded wastewater flow P = Population in thousands. BIOCHEMICAL OXYGEN DEMAND (BOD) Biochemical Oxygen Demand (BOD) is a measure of the oxygen required by microorganisms in the biochemical oxidation (digestion) of organic matter. BOD is an indicator of the organic strength of the wastewater. If BOD is discharged untreated to the environment, biodegradable organics will deplete natural oxygen resources and result in 6-4 City of Marysville November 2011 Sewer Comprehensive Plan the development of septic (anaerobic) conditions. BOD data together with other parameters are used in the sizing of the treatment facilities and provide a measurement for determining the effectiveness of the treatment process. BOD is expressed as a concentration in terms of milligrams per liter (mg/L) and as a load in terms of pounds per day (lb/d). The term BOD typically refers to a 5-day BOD, often written BOD5, since the BOD test protocol requires five days for completion. BOD5 of a wastewater is composed of two components – a carbonaceous oxygen demand (CBOD5) and a nitrogenous oxygen demand (NBOD5). The use of CBOD5 as a parameter for evaluating wastewater strength removes the influence of nitrogenous components, including ammonia and organic nitrogen. As shown in Chapter 5, the NPDES permit for the City of Marysville WWTP includes effluent limits expressed in terms of CBOD5, and influent limits expressed in terms of BOD5. SUSPENDED SOLIDS Suspended Solids is the solid matter carried in the waste stream. The Total Suspended Solids (TSS) in a wastewater sample is determined by filtering a known volume of the sample, drying the filter paper and measuring the increase in weight of the filter paper. TSS is expressed in the same terms as BOD; milligrams per liter for concentration and pounds per day for mass load. The amount of TSS in the wastewater is used in the sizing of treatment facilities and provides another measure of the treatment effectiveness. The concentration of TSS in wastewater affects the treatment facility biosolids production rate, treatment and storage requirements, and ultimate disposal requirements. CHLORINE Chlorine is a chemical element that acts as a strong oxidant when exposed to certain components of organic matter. Chlorine is widely used as a disinfectant in wastewater treatment, and is available both in gaseous (elemental chlorine) and solution forms (hypochlorite). Chlorine is a toxic chemical and is lethal to aquatic biota if present in too high a concentration. Additionally, some organic constituents may react with the chlorine to interfere with chlorination or form toxic compounds, such as chloroform, that can have long-term adverse effect on the beneficial uses of the waters to which they are discharged. To minimize the effects of potentially toxic chlorine residuals on the environment, it has sometimes been found necessary to dechlorinate wastewater treated with chlorine or substitute alternative disinfection systems such as ultraviolet disinfection. ULTRAVIOLET DISINFECTION Ultraviolet disinfection is used as a reliable means of disinfection in the wastewater industry. In UV disinfection, contaminated water is exposed to special lamps that generate radiation. The lamps create UV light by striking an electric arc through low- pressure mercury vapor. The lamps emit a broad spectrum of radiation to destroy bacteria between 250nm and 270nm (nanometers). The treatment works because UV light City of Marysville 6-5 Sewer Comprehensive Plan November 2011 penetrates an organism’s cell walls and disrupts the cell’s genetic material, making reproduction impossible. SAND FILTER Sand filters can be used for many applications including denitrification, phosphorus removal, algae filtration, and turbidity reduction. The Dynasand Filter is a continuous-backwash, upflow, deep-bed, granular media filter. Filter media is continuously cleaned by recycling the sand internally through an airlift pipe and sand washer. The cleansed sand is redistributed on top of the sand bed, allowing for an uninterrupted flow of filtrate and reject (backwash water). Feed is introduced at the bottom of the filter and flows upward through the sand bed bottom. Solids are trapped in the sand bed and the filtrate exits over the effluent weir. The sand bed, along with the accumulated solids, is drawn downward into an airlift pipe. Compressed air, introduced at the bottom of the airlift, draws sand into the airlift, scours it, and rejects the backwash water. OTHER CONTAMINANTS OF CONCERN Other contaminants of concern in wastewater include nutrients, priority pollutants, heavy metals and dissolved organics. The City’s NPDES permit requires the removal of biodegradable organics (CBOD5), ammonia, suspended solids and pathogens. Nutrients such as ammonia, other forms of nitrogen and phosphorus, along with carbon, are essential requirements for growth. When discharged to the aquatic environment, these nutrients can lead to the growth of undesirable aquatic life. When discharged in excessive amounts on land, they can also lead to the pollution of groundwater. Additionally, in too high a concentration, nutrients, particularly ammonia, can be toxic to aquatic life. Priority pollutants are organic and inorganic compounds selected on the basis of their known or suspected carcinogenicity, mutagenicity, teratogenicity, or high acute toxicity. Many of these compounds are found in wastewater. Inorganic constituents, including heavy metals, are often present in wastewater due to commercial and industrial activities and may have to be removed from the wastewater if the presence of the metals will adversely affect the receiving water, or, if the wastewater is to be reused. Some heavy metals (most notably copper) can be present in wastewater due to leaching from drinking water pipes. EXISTING WASTEWATER FLOWS AND LOADING WWTP records for the five-year period from 2006 through 2010 have been reviewed and analyzed to determine current wastewater characteristics and influent loadings. Current 6-6 City of Marysville November 2011 Sewer Comprehensive Plan wastewater flows and loadings are used in conjunction with projected population data to determine projected future wastewater flows and loadings. HISTORICAL WASTEWATER FLOWS AND LOADINGS AT CITY OF MARYSVILLE WWTP Table 6-1 summarizes WWTP influent flows for the 5-year period of 2006 - 2010. The reported monthly average influent WWTP flows ranged from 3.92 mgd to 6.12 mgd. Following the 2004 Phase I and Phase II upgrades to the wastewater treatment plant, it was discovered that by removing the Parshall Flume fiberglass insert that had been in use since the 1994 upgrades, that the concrete structure that was intended to be used as flows increased, was not poured uniformly and did not provide accurate combined influent flow measurements from Trunks A and C. For this reason, influent flows are measured using the Trunk A Palmer Bowlus flume, and the Trunk C Magnetic Flow Meter. Those flows are combined for the total combined influent as reported on the discharge monitoring reports. For the purposes of this Plan, influent flows reported on the DMRs are utilized. TABLE 6-1 Historical WWTP Influent Flows(1) (2006-2010) Flow Flow Rate (mgd) Average Dry Weather Flow(2) 4.16 Annual Average Flow 4.73 Maximum Month Flow(3) 6.12 Peak Day Flow(4) 9.31 Peak Hour Flow(5) 10.7 (1) Based on Monthly Influent flows as reported on the WWTP DMRs. (2) Average of July, August, September from 2006-2010, as described in the text. (3) Reported for June 2010 (4) Reported for June 9, 2010 (5) Calculated using Ecology’s Orange Book Figure C1-1: Q peak hourly = 18 + square root (P) = 18 + 7.11 = 2.3 Q design average 4 + square root (P) 4 + 7.11 Where P = 50.543 (50,543 sewered population) Peak Hour Flow = 4.73 mgd x 2.26 = 10.7 mgd Monthly discharge monitoring report (DMR) data for this period are summarized in Table 6-2. Graphical representations of average monthly WWTP flows, influent BOD5 and TSS loadings, and effluent CBOD5 concentrations and maximum peak weeks for the period from January 2006 through December 2010 are shown in Figures 6-1, 6-2, and 6- 3, and 6-4, respectively. ! "#"!$ ! "# ! "#%&’(( )*+"(( )*+"(( )*+"(( )*+"(( )*+" !"## "##$%%#&’%(((%(#&(’(%$$$%$#&$’$%)))%)#&)’)%%#&’ !" !"##$%&#’’’#’$%’&’#(((#($%(&(#)))#)$%)&)##$%& !"##$% !!$&’’()*’+++’+()+*+’,,,’,(),*,’---’-()-*-’’()*!$& City of Marysville 6-7 Sewer Comprehensive Plan November 2011 TABLE 6-2 Summary of Discharge Monitoring Reports (DMR’s) WWTP Influent and Effluent Monthly Averages Date Influent Flow Influent Influent Eff Flow Eff Flow Eff CBOD5 Eff CBOD5 mgd avg mgd Peak day BOD5 TSS mgd mgd mg/L mg/L mg/L lb/d mg/L lb/d avg peak mo avg Peak week Jan-06 6.06 7.57 245 12227 279 13911 5.62 6.05 7 9 Feb-06 5.97 6.48 195 9686 247 12390 5.22 5.73 9 11 Mar-06 5.38 6.16 232 10365 270 12107 4.74 5.04 11 16 Apr-06 5.58 6.30 296 13812 308 14356 4.68 5.24 14 20 May -06 4.90 5.72 280 11128 273 10820 4.14 5.20 12 17 Jun-06 4.95 5.66 261 10739 284 11683 4.10 5.79 13 15 Jul-06 4.51 4.76 361 13760 318 12131 3.35 4.60 10 13 Aug-06 4.00 4.49 333 11070 326 10842 3.14 4.12 7 9 Sep-06 4.39 5.18 322 11984 278 10368 3.93 4.95 10 12 Oct-06 4.59 5.14 320 12127 295 11314 3.61 4.84 8 10 Nov-06 5.70 6.71 235 10923 261 12172 5.81 7.45 8 12 Dec-06 5.89 7.62 237 11709 267 13255 5.67 6.62 11 13 Jan-07 5.83 6.70 203 9729 202 9748 5.35 6.25 10 13 Feb-07 5.54 6.61 222 10004 247 11151 5.15 6.86 10 16 Mar-07 5.22 6.51 199 8454 171 7466 5.54 6.58 7 8 Apr-07 4.88 6.37 249 10202 206 8451 5.40 6.50 11 12 May-07 4.21 4.60 282 10166 227 8183 4.39 5.44 11 15 Jun-07 4.09 4.70 305 10560 284 9880 4.02 5.08 9 12 Jul-07 4.14 4.25 315 10973 255 8868 3.54 4.98 10 14 Aug-07 4.03 4.30 304 10391 248 8481 3.55 4.40 8 13 Sep-07 4.04 4.24 281 8858 213 7286 3.59 4.07 10 11 Oct-07 4.07 4.47 318 10908 300 10249 3.92 4.73 7 8 Nov-07 4.04 4.50 334 11246 275 9245 3.99 4.63 6 7 Dec-07 4.93 6.82 274 11157 247 10075 5.46 6.92 9 13 Jan-08 4.89 5.40 240 9752 180 7341 5.14 6.69 12 14 Feb-08 4.70 5.23 297 11513 276 10677 5.11 6.33 10 10 Mar-08 4.69 6.16 296 11237 221 8393 4.86 6.04 10 12 Apr-08 4.83 5.15 241 9673 225 9017 5.11 6.44 10 15 May-08 4.57 5.27 231 8977 202 7850 4.53 5.55 10 13 Jun-08 4.42 4.84 296 11070 243 9143 4.25 5.47 9 11 Jul-08 4.07 4.36 353 12113 260 8946 3.58 5.44 10 13 Aug-08 4.03 4.57 242 8250 226 7695 3.63 5.33 9 12 Sep-08 4.00 4.28 336 11244 320 10716 3.53 4.98 11 12 Oct-08 4.01 4.55 289 9601 251 8338 3.74 4.79 14 20 Nov-08 4.84 6.58 297 11933 246 9945 3.33 4.66 12 14 Dec-08 4.89 6.82 300 11867 239 9522 5.22 6.87 11 17 6-8 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 6-2 – (continued) Summary of Discharge Monitoring Reports (DMR’s) WWTP Influent and Effluent Monthly Averages Date Influent Flow Influent Influent Eff Flow Eff Flow Eff CBOD5 Eff CBOD5 mgd avg mgd Peak day BOD5 TSS mgd mgd mg/L mg/L mg/L lb/d mg/L lb/d avg peak mo avg Peak week Jan-09 5.61 8.05 241 11349 220 10637 6.15 8.27 17 22 Feb-09 4.36 4.61 281 10155 232 8376 4.46 4.59 14 16 Mar-09 4.57 5.23 264 10063 207 7881 4.83 5.61 9 12 Apr-09 4.98 5.99 239 9823 284 11754 5.15 6.69 13 16 May-09 4.63 5.36 252 9989 238 9456 4.63 7.22 13 16 Jun-09 4.19 4.52 244 8534 275 9635 3.79 4.97 9 11 Jul-09 3.97 4.08 322 10744 312 10395 3.40 4.52 10 15 Aug-09 3.99 4.20 342 11475 306 10261 3.49 5.24 9 12 Sep-09 3.92 4.17 271 8864 274 8944 3.39 5.13 10 12 Oct-09 4.22 5.77 285 9693 304 10310 4.17 5.46 7 8 Nov-09 5.09 7.09 252 10842 285 12306 3.66 4.82 7 7 Dec-09 4.87 7.38 252 10219 277 11358 4.49 5.79 8 13 Jan-10 5.42 6.43 193 8853 216 9962 5.37 6.68 7 8 Feb-10 4.91 5.64 210 8583 254 10405 4.70 6.39 8 12 Mar-10 4.78 5.75 218 8611 238 9400 4.89 5.82 13 16 Apr-10 5.06 5.89 262 11318 311 13441 4.78 6.74 10 12 May-10 4.85 6.33 229 8951 241 9456 4.63 6.41 11 12 Jun-10 6.12 9.31 204 10488 209 10861 6.13 9.19 7 9 Jul-10 4.53 4.90 239 9141 229 8783 3.98 4.35 7 9 Aug-10 4.25 4.98 280 10143 269 9731 3.75 5.12 8 9 Sep-10 4.48 5.33 249 9363 252 9484 4.47 5.96 7 8 Oct-10 4.26 4.65 245 8744 229 8135 4.16 5.44 6 8 Nov-10 4.86 5.82 201 8124 185 7470 4.94 7.00 8 11 Dec-10 5.26 6.69 264 11683 255 11298 5.58 7.02 9 16 Average 4.73 5.62 268 10419 255 10029 4.48 5.75 10 13 Maximum 6.12 9.31 361 13812 326 14356 6.15 9.19 17 22 Minimum 3.92 4.08 193 8124 171 7286 3.14 4.07 6 7 The 5-year coverage concentrations for Influent BOD5 and TSS are 268 mg/L and 255 mg/L respectively. The average monthly concentrations for Influent BOD5 covered a range from 193 mg/L to 361 mg/L over the period from 2006 to 2010. Similarly, average monthly concentrations for Influent TSS covered a range from 171 mg/L to 326 mg/L. Average and maximum monthly concentrations in these ranges would be considered low to medium strength domestic wastewater. City of Marysville 6-9 Sewer Comprehensive Plan November 2011 The maximum monthly Influent BOD5 loading shown in Table 6-2 is 13,812 lb/d for April 2006. Being as other monthly averages for BOD5 loading were well below 13,812 lb/d, this value is considered representative of maximum month conditions. As discussed below in the “Existing BOD5 Loading” section, use of this maximum month loading value yields a relatively high per capita loading value of 0.310 lb/cap/d, and 0.699 lb/ERU/d, respectively. The ratio of the maximum month BOD5 loading to the annual average BOD5 loading is 1.33 to 1. This ratio is used in the calculation of future loadings to the plant. The maximum monthly Influent TSS loading shown in Table 6-2 is 14,356 lb/d for April 2006. Since other monthly averages (13,911 lb/d in January 2006 and 13,441 lb/d in April 2010) were well below this value, this value is considered representative of maximum month conditions. The ratio of maximum month TSS loading to annual average TSS loading is 1.43 to 1. This ratio is used in the calculation of future loadings to the plant. The annual average and maximum month influent BOD5 and TSS mass loading, along with annual average effluent and influent flows, for 2006 through 2010 are listed in Table 6-3. TABLE 6-3 WWTP Flow and Loading Summary(1) Year Annual Average Influent Flow (mgd) Annual Average Effluent Flow (mgd) Annual Average Influent BOD5 (lb/d) Annual Average Influent TSS (lb/d) Maximum Month Influent BOD5 (lb/d) Maximum Month Influent TSS (lb/d) 2006 5.16 4.50 11,628 12,112 13,812 14,356 2007 4.59 4.49 10,221 9,090 11,246 11,151 2008 4.50 4.34 10,603 8,965 12,113 10,716 2009 4.53 4.30 10,146 10,109 11,475 12,306 2010 4.90 4.78 9,500 9,869 11,683 13,441 Average(1) 4.74 4.48 10,420 10,029 12,066 12,394 (1) Average of yearly averages. Changes in influent BOD5 and TSS loadings have generally correlated with changes in influent flows. Annual average influent flows and loadings decreased from 2007 to 2009 relative to 2006. Flows began to increase in 2010 although loadings remained nearly as low or lower than previous years. 6-10 City of Marysville November 2011 Sewer Comprehensive Plan EXISTING EQUIVALENT RESIDENTIAL UNITS (ERUS) To determine the number of residential units with sewer service, water consumption, water billing and sewer billing records were reviewed. WATER CONSUMPTION Water use (consumption) is used to estimate wastewater volumes entering the collection system because the amount of water use typically is equal to wastewater flow except for an amount of water that does not enter the sewer system (such as irrigation flows). Table 6-4 presents the number of total water accounts, the number of total sewer accounts and the total number of sewer only accounts (no water). For single family residential, there were 14,405 sewer accounts of which 12,234 of these accounts also received water (the difference of 14,405 and 2,171). It is this percentage of single family (12,234 divided by 16,581) by which Table 6-4 presents water use from all 16,581 single family accounts and water use from all 12,234 single family accounts receiving City water. The table also presents the same for multi-family, school and commercial. Table 6-4 also presents the annual average water consumption in gallons per day (gpd) by customer class for 2010. For this analysis, flows from querying the City’s billing database for the various customer classes are used. For the summary of water use presented in Table 6-4, the customer classes have been combined into four categories. TABLE 6-4 2010 Annual Average Water Use by Customer Class Customer Grouping Water Accounts Sewer Accounts Sewer Only Accounts Percent Difference Single Family Residential 16,581 14,405 2,171 73.8% Multi Family Residential 840 698 9 82.0% School 49 32 0 65.3% Commercial 933 827 0 88.6% Customer Grouping Water Use (gpd) Water Use (gpd) by Combined Sewer-Water Accounts Single Family Residential 2,695,353 2,342,262 Multi Family Residential 676,301 562,006 School 172,666 112,751 Commercial 1,407,696 1,247,219 TOTAL 4,952,016(1) 4,264,238 (1) Compared to a 2010 average of 4.14 MGD based on metered water consumption data. City of Marysville 6-11 Sewer Comprehensive Plan November 2011 Table 6-5 provides average water consumption for the City’s major water consumers. TABLE 6-5 Major Water Consumers for 2010 Customer 2010 Annual Average Consumption (gpd) % of Total Annual City Water Consumption(1) 1 Pacific Coast Feather Co. 78,093 1.9% 2 National Food Corp 34,962 0.8% 3 Marysville Care Center 10,677 0.3% 4 Captain Dizzy Car Wash 10,548 0.3% 5 Marysville YMCA 9,337 0.2% 6 Fred Meyer Inc 8,512 0.2% 7 Medallion Hotel 8,419 0.2% 8 Holiday Inn Express 8,263 0.2% 9 Haggen Food & Pharmacy 8,104 0.2% 10 Northwest Composites 7,660 0.2% TOTAL 184,575 4.5% EQUIVALENT RESIDENTIAL UNITS Use of Equivalent Residential Units (ERUs) is a method to express the amount of water or sewer use by non-residential customers as an equivalent number of residential customers. The water consumption ERU value is calculated by dividing the total volume of water utilized in the single-family residential (SFR) customer class by the total number of active single-family residential connections. The wastewater ERU value is calculated based on water use. For typical wastewater collection systems, it is estimated that, depending on the City, anywhere from 0 percent (negligible) to as much as 15 percent of the water consumption does not enter the wastewater collection system. The wastewater ERU value is calculated by dividing the water use for single family residential units by the number of single family units and multiplying by the fraction of water estimated to enter the sewer (0.85 to 1.00). The average daily volume of water used by other customer classes can then be multiplied by this factor and divided by the average daily single- family residential water use to determine the number of equivalent residential units consumed by other customer classes. With 12,234 single-family residences receiving water and sewer service and an estimated 2,342,262 gpd water consumed by these customers (per Table 6-4), the average daily single-family residential water use (which is equivalent to one ERU) for the City in 2010 was 191 gpd/ERU. Since the water use records account for annual average, for planning purposes it is estimated that 5% of water does not enter the sewer system. Therefore, the estimated water entering the sewer system from single-family residential use is 2,225,150 6-12 City of Marysville November 2011 Sewer Comprehensive Plan gpd and the average daily single-family residential water use (which is equivalent to one ERU) for the City in 2010 is 182 gpd/ERU. Table 6-6 summarizes current wastewater ERUs based on an analysis of water use. As shown in Table 6-6, the total water use among the combined City sewer/water customers was 4.45 mgd in 2010. This is less than the annual average influent sewage flow (4.73 mgd) as determined by analysis of the DMRs which indicates I/I. The second column in this table shows water use for customers who receive both sewer and water service from the City; as in Table 6-4, this does not include water use by water- only customers. The third column provides the estimated additional sewage flow discharged from customers who receive sewer service, but not City water service. In 2010, there were 2,169 residential sewer-only accounts within the City and 2 residential sewer-only accounts outside City limits. There were 9 multi-family residential sewer- only accounts. This additional sewage flow was estimated by multiplying the per connection water use by the number of sewage service connections that are not provided water service. The fourth column provides a sum of water use and sewage flow from sewer-only customer. The fifth and six columns show the estimated number of ERUs and percentage of total ERUs, respectively, for each customer class. TABLE 6-6 Current Wastewater ERUs Water Use By Combined Sewer-Water Customers Minus 5% (gpd) Estimated Additional Flow from Sewer-Only Customers (gpd) (1) Sum of Water Use and Estimated Additional Flow from Sewer-Only Customers (gpd) Sewer ERUs(1) % of Total ERUs Single Family Residential 2,225,150 392,951 2,618,101 14,385 58.9% Multi Family Residential 533,906 1,629 535,535 2,943 12.0% School 107,113 (0) 107,113 589 2.4% Commercial 1,184,858 (0) 1,184,858 6,510 26.7% TOTAL 4,051,027 4,445,607 24,427 100.0% (1) Based on 182 gpd/ERU INFILTRATION AND INFLOW The amount of infiltration and inflow (I/I) can be estimated on an annual average, maximum month, and maximum day basis by subtracting the dry weather flow at the WWTP from the annual average, maximum month, and maximum day flows at the WWTP. City of Marysville 6-13 Sewer Comprehensive Plan November 2011 For this Plan, infiltration and inflow is expressed in units of gallons per acre per day (gpad). The average developed sewer service area, which includes the majority of the City and portions of its UGA, for the period of analysis, is comprised of approximately 4,979 acres from parcels. The total acreage of the UGA is approximately 13,660 acres. Areas designated for recreation and open space and unsewered areas are excluded from the total acreage to estimate the developed sewer service area. Table 6-7 summarizes the infiltration/inflow analysis. The data contained in this table is useful as a baseline for evaluating changes in infiltration and inflow in the future. This data is also used to estimate future flows. Infiltration and Inflow Analysis using EPA criteria Another analysis of infiltration and inflow was performed to compare estimates of per capita I/I to EPA criteria. These infiltration and inflow rates are summarized in Table 6- 8. TABLE 6-7 Estimated Infiltration and Inflow Flow Influent Flow at WWTP (mgd) Base Flow (mgd) (1) I/I (mgd) Service Area (acre)(3) I/I (gpad) Dry Weather (July – Sept.) 4.16 4.45 0 4,979 0 Annual Average 4.73 4.45 0.28 4,979 56 Max. Month 6.12 4.45 1.67 4,979 335 Peak Day 9.31 4.45 4.86 4,979 976 Peak Hour 10.7 5.5(2) 5.2 4,979 1,044 (1) Base flow as estimated in Table 6-6 (2) The one hour peak flow during a day with average dry weather peak flow (4.16 mgd) (3) Estimate of developed, sewered parcels only in the Marysville sewer service area. The U.S. EPA manual entitled I/I Analysis and Project Certification provides recommended guidelines for determining if infiltration and/or inflow is excessive. 1. To determine if excessive infiltration is occurring, a threshold value of 120 gallons per capita per day (gpcd) is used. This infiltration value is based on an average daily flow over a seven to fourteen day non-rainfall period during seasonal high ground water conditions. 2. To determine if excessive inflow is present in a collection system, the USEPA uses a threshold value of 275 gpcd. If the average daily flow (excluding major commercial and industrial flows greater than 50,000 gpd 6-14 City of Marysville November 2011 Sewer Comprehensive Plan each) during periods of significant rainfall exceeds 275 gpcd, the amount of inflow is considered excessive. Infiltration WWTP precipitation records show a 6-day period, November 28 through December 3, 2006 during which no rainfall was measured. This would also be a period of relatively high groundwater due to a total rainfall of over seven inches earlier in November. The average daily flow recorded during this time period was 5,410,000 gallons per day. (The highest daily flow was 5,660,000 gpd.) Since the intent of the EPA criteria was to only include domestic flows, 1,444,470 gpd (26.7 percent of the baseflow) for commercial flow was neglected. With a total population of sewer users of 50,543 and a residential flow of 3,965,530 gpd (equal to 5,410,000 gpd minus 1,444,470 gpd) for this period, the peak infiltration is estimated at 78 gpcd. Because this value is less than the EPA guideline of 120 gpcd, Marysville is not considered to have excessive infiltration by EPA criteria. Inflow The maximum day flow at the WWTP over the period of 2006 - 2010 was 9.31 mgd (recorded in June, 2010), as shown in Table 6-2. Since the intent of the EPA criteria was to only include domestic (residential) flows, 2.46 mgd (26-percent of the 9.31 mgd) of commercial flow was neglected. With an estimated total population of sewer users in 50,543, and a non-commercial flow of 6,850,000 gpd (equal to 9,310,000 gpd minus 2,460,000 gpd) for this day, the residential peak inflow is estimated at 136 gpcd. Because this value is less than the EPA guideline of 275 gpcd, the City is not considered to have excessive inflow by EPA criteria. Flow Monitoring There was no flow monitoring performed as an update to this Plan. I/I Summary In general, I/I for the City’s sewer collection system can be considered a moderate problem. Based on EPA criteria, I/I is not considered excessive but on an annual average basis, I/I represents about 6 percent of the total wastewater flow. Yet because of the large area covered by the collection system, I/I is only 56 gpad as presented in Table 6-7. I/I contributions increase to 335 gpad during maximum month periods, or about 27 percent of the total flow. I/I values typically cover a range of 20 to 3,000 gpad (Wastewater Engineering Treatment Disposal and Reuse, Metcalf and Eddy, Inc., 3rd Edition). For the City’s flows, I/I values fall at the low end of this range. Another indicator of I/I is related to the concentration of BOD5. The influent BOD5 concentration is medium strength indicating relatively low levels of I/I. High I/I flows City of Marysville 6-15 Sewer Comprehensive Plan November 2011 will dilute the strength of BOD5 but the DMR data shows relatively little difference between dry and wet weather concentrations. For the 5-year period presented in Table 6-2, the average dry weather (July, August, and September) BOD5 concentration was 303 mg/L, and the average wet weather (December, January, and February) BOD5 concentration was 231 mg/L, a difference of 23 percent. TABLE 6-8 Per Capita Infiltration and Inflow Based on EPA Criteria Parameter EPA Criteria for Excessive I/I (gpcd) Estimated Marysville I/I Value (gpcd) EPA Excessive Infiltration Criteria 120 78 EPA Excessive Inflow Criteria 275 136 PROJECTED SEWER SERVICE AREA POPULATION, ERU AND FLOWS As discussed in Chapter 3, an estimated population of 50,543 (44,372 Single Family Residential plus 6,172 Multi-Family) out of the total service area population of 64,669 within the sewer service area was provided sewer service by the City in 2010, while the total population estimated to be served by the City’s sewer system in 2010 was 61,491. The current and projected 6-year and 20-year ERUs and flows are summarized in Table 6-9. The projected flows and ERUs are based on the growth rates developed in Table 3- 11, including the following assumptions: • In the existing sewer system, the I/I contribution to the WWTP will increase with increases in the age of the sewer system and the size of the service area. The increase with system age accounts both for deterioration of system components with time, as well as assumed increased density, and thus overall pipe length, that occur with time. • For the existing sewer service area, the 2011 peak day I/I rate shown in Table 6-7 increases at a linear rate to 1,000 gpad over the next 20 years. New sewer service area served will be assumed to have a peak day I/I rate of 100 gpad I/I initially, increasing at a linear rate to 1,000 gpad over 50 years. • For the existing sewer service area, the other I/I rates – dry season, annual average, maximum month, and peak hour – grow at the sewer population 6-16 City of Marysville November 2011 Sewer Comprehensive Plan growth rates determined in Chapter 3. New sewer service area served will be assumed to have a lower – dry season, annual average, maximum month, and peak hour – I/I rate initially, increasing at the sewer population growth rates determined in Chapter 3. • To estimate future dry season, annual average, maximum month, and peak day flows, the projected I/I flowrates are added to the base level wastewater flows derived from the population projections to obtain the respective future WWTP influent flowrates. As shown in Table 6-9, the projected year 2031 maximum month flow is 11.25 mgd, which is below the rated hydraulic capacity of the WWTP (12.7 mgd after completion of Phase 2 improvements in 2004.) TABLE 6-9 Current and Projected Future Wastewater Flows (gpd) Year 2010 2017 2031 ERUs 24,427 30,084 42,413 Sewer Service Area(1) 4,979 5,708 7,340 Total Baseflow 4,030,000 5,480,000 7,720,000 Dry Season Average Flow 4,160,000 5,240,000 7,620,000 Average Annual Flow 4,730,000 5,830,000 8,230,000 Maximum Month 6,120,000 7,600,000 11,250,000 Peak Day 9,310,000 10,530,000 13,790,000 Peak Hour(2) 10,700,000 12,710,000 16,880,000 Peak Hour Factor(3) 2.26 2.18 2.05 (1) In acres, per Chapter 7. (2) Peak Hour: Average Annual Flow x Peak Hour Factor (3) See Table 6-1 for Peak Hour Factor calculation. See Chapter 7 for populations. City of Marysville 6-17 Sewer Comprehensive Plan November 2011 EXISTING AND PROJECTED INFLUENT BOD5 AND TSS LOADING EXISTING BOD5 LOADING Monthly average influent BOD5 loadings ranged from 8,124 lb/d to 13,812 lb/d for the 5- year period of analysis as shown in Table 6-2 and Figure 6-1. The average influent BOD5 concentration for the 5-year period is 268 mg/L, which would be considered medium strength domestic wastewater. The average loading of 10,419 lb/d (see Table 6-2) and an average sewer service population of 48,200 for the 5-year time period of 2006-2010 translate to an average BOD5 loading of 0.227 lb/cap/d. This value is just slightly higher than the DOE Orange Book criteria of 0.2 lb/cap/d, possibly due to industrial and commercial loading. To convert the current maximum month BOD5 loading to a per capita and an ERU basis, the service population of 48,200 and number of ERUs (24,427) and maximum month BOD5 of 13,812 lb/d for the 5-year analysis period were used to calculate a maximum month per capita and ERU BOD5 loading of 0.287 lb/cap/d and 0.565 lb/ERU/d, respectively. The ratio of the maximum month BOD5 loading to the annual average BOD5 loading is 13,812 : 10,419 or 1.33:1. This ratio is used in the development of future loadings to the WWTP later in the chapter. EXISTING TOTAL SUSPENDED SOLIDS LOADING A review of Table 6-2 shows that monthly average TSS loadings ranged from 7,286 lb/d to 14,356 lb/d. The average month loading of 10,029 lb/d and an average population and average ERUs of 48,200 and 24,427, respectively, for the 5-year time period translate to an average month TSS loading of approximately 0.208 lb/cap/d or 0.411 lb/ERU/d. The maximum month TSS loading is 14,356 lbs/d. Using the same population and ERU values as derived for the BOD analysis, this approach results in a current maximum month value of 0.298 lbs TSS/cap/d or 0.588 lb/ERU/d. The ratio of the maximum month TSS loading to the annual average TSS loading is 14,356 : 10,029 or 1.43:1. This ratio is used in the development of future flow and loadings to the WWTP later in the Chapter. PROJECTED WASTEWATER LOADINGS Future WWTP maximum month BOD5 and TSS loadings are estimated by multiplying the projected ERUs by the respective ERU-based loadings. Future annual average BOD5 and TSS loadings are estimated using the ratio of the maximum month to annual average loadings of these parameters. The current maximum month BOD5 and TSS loadings are 0.565 lb BOD5/ERU/d and 0.588 lb TSS/ERU/d. The ratio of the maximum month to annual average BOD5 is 1.33:1. The ratio of the maximum month to annual average TSS 6-18 City of Marysville November 2011 Sewer Comprehensive Plan is 1.43:1. Table 6-10 provides a summary of projected future WWTP influent BOD5 and TSS loadings. The projected year 2017 loadings are less than the design capacity of the WWTP for both BOD and TSS. The year 2031 maximum month loading for BOD5 (23,963 lb/d) exceed the rated capacity of 20,143 lb/d BOD5, and the year 2031 maximum month loading for TSS (24,939 lb/d) exceed the rated capacity of 24,229 lb/day (Table 5-5). TABLE 6-10 Current and Projected WWTP Loadings ERUs/Loading 2010 2017 2031 ERUs 24,427 30,084 42,413 Annual Average BOD5, lb/d 10,419 12,846 18,110 Max Month BOD5, lb/d 13,812 16,997 23,963 Annual Average TSS, lb/d 10,029 12,365 17,432 Max Month TSS, lb/d 14,356 17,689 24,939 INDUSTRIAL WASTEWATER The City’s major industrial wastewater producers currently account for approximately 225,000 gpd or about 5.5% of the daily flow. Table 6-11 summarizes the City’s major Industrial Wastewater Producers for 2011 and includes operating hours, industrial process, estimated wastewater volume per day and wastewater characteristics. The City is currently not affected by these significant industrial users. However, they do have the potential to discharge high BOD, TSS and heavy metals if their pretreatment systems are not maintained. Significant industrial users that have pretreatment systems in place are required to have a discharge permit with Department of Ecology. In addition, the City also tests and monitors pretreatment systems monthly or quarterly. Much of the City’s industrial zoning is concentrated in the Smokey Point neighborhood and within the southerly portion of the Downtown neighborhood. (Refer to Figure 3-1 and Figure 3-3). Light industrial, as described in Chapter 3, is zoned for in the Smokey Point neighborhood. General Industrial, as also described in Chapter 3, is zoned for in the Downtown neighborhood. Most of the available General Industrial land available in the Downtown neighborhood is occupied. There is approximately 750 acres (out of 1,100 total) of available land for light industrial in the Smokey Point neighborhood. Based on modeling at 2,700 gpd/acre, this could equate to approximately 2.0 MGD of wastewater from the light industrial. This flow has been accounted for in the modeling efforts described in Chapter 7 and therefore the existing sewer infrastructure is modeled to account for the expansion of light industrial. City of Marysville 6-19 Sewer Comprehensive Plan November 2011 Certain industrial wastewater processes will carry pollutants or levels of certain pollutants which are prohibited to discharge to the City’s sewer system and could cause detriment to the City’s WWTP. Therefore, before discharging to the City’s sewer system, the industrial wastewater must undergo pretreatment. Such significant industrial users would be subject to wastewater pretreatment in accordance with Chapter 14.20 MMC. TABLE 6-11 City of Marysville Industrial Wastewater Producers - 2011 Industrial Users Operating Shifts Hours/Days Process Wastewater Volume gallons/day Wastewater Characteristics 1 Aerocell Inc. 24 Hours Weekdays 16 Hours Weekends Honey comb composite manufacturing 3,000 – 5,000 Discharges from bathrooms only. No pretreatment facility. Spill protection plan in place for oils. 2 Artisan Finishing 5 Days Week 0630 – 1530 Kynar Coating of Architectural Metals 2,000 Discharges from bathrooms and manufacturing process. Pretreatment includes a clarifier and pH adjustment. 3 B.E. Aerospace 12 Hour Day 0600 - 1400 Design, certification and manufacturing of aircraft standard components. 3,000 Discharges from bathrooms, kitchen, floor drains and an abrasive water jet cutter. Spill plan in place. 4 C & D Zodiac 24 Hours Day Aircraft part manufacturing 8,000 Discharges from bathrooms and manufacturing process including water from plaster casting and cleaning of spray guns for water soluble adhesives. No pretreatment facility. Spill protection plan in place for oils. 5 Centralia Fur and Hide 5 Days Week 0700 - 1530 Leather Manufacturing including processing of animal hides and hair removal 5000 - 10,000 Discharges from manufacturing process. Pretreatment includes aeration and settling tanks. 6 Iversen Distributing 24 Hours Day Warehouse and distribution center for dairy products. 2,000 Discharges from bathrooms only. No processing of dairy products at this site. 6-20 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 6-11 Cont… City of Marysville Industrial Wastewater Producers - 2011 Industrial Users Operating Shifts/ Hours/Days Process Wastewater Volume gallons/day Wastewater Characteristics 7 Metal Finishing, Inc. 16 Hours Day 0730 - 2300 Cleaning, conversion coating, anodizing and tin plating of metals. 3,000 – 5,000 Discharges from bathrooms and manufacturing process. Pretreatment includes batch treatment for Chrome containing solutions and pH adjustment. 8 National Foods Corporation 7 Days Week 20 Hours Day 0300 -0100 Whole egg and egg product processing 50,000 – 60,000 Discharges from bathrooms and manufacturing process. Pretreatment includes a poly based coagulation system for BOD/TSS removal and clarifier and pH adjustment 9 Pacific Coast Feathers 4 Days Week 0700 – 1700 Washing, drying and separating down from feather material. 70,000 – 120,000 Discharges from bathrooms and manufacturing process. Pretreatment includes a hydroscreen to separate down form feathers and a clarifier and pH adjustment 10 Pacific Grinding Wheel 5 Days Week 0730 - 1630 Grinding wheel manufacturing 2,600 Discharges from bathrooms, kitchen and clean up sink in the vitrified mixing area. No pretreatment facility. Spill protection plan in place for oils. 11 Sea Cast, Inc 18 Hours Day 0800 - 0200 Stainless Steel investment casting 4,000 Discharges from bathrooms and manufacturing process. Pretreatment facility includes a system for neutralizing rinse water and removing metals. 12 Thomas Machine & Foundry 20.5 Hours Day 0500 - 0130 Aluminum Castings and Machining 700 – 1,000 Discharges from bathrooms, kitchen, floor drains and vibratory tumbler. No Pretreatment facility. City of Marysville 6-21 Sewer Comprehensive Plan November 2011 REFERENCES 1. Comprehensive Sanitary Sewerage Plan, City of Marysville , HCWL, October 1990 2. Comprehensive Sanitary Sewerage Plan, City of Marysville , HCWL, KCM, Jones and Stokes, June 1997 3. Sanitary Sewer Infiltration / Inflow Analysis, HCWL, September 1999 4. Wastewater Treatment Plant Capital Facilities Plan, Final, February 2001, KCM 5. Comprehensive Sanitary Sewerage Plan, City of Marysville , G&O, May 2005 City of Marysville 7-1 Sewer Comprehensive Plan November 2011 CHAPTER 7 COLLECTION SYSTEM EVALUATION INTRODUCTION The purpose of the hydraulic/hydrologic analysis is to evaluate the City’s sewer collection system based on existing and future conditions. Existing and future population, land use, and wastewater flows presented in Chapters 3 and 6 of this Plan are utilized to develop data for use in the hydraulic model. Total area population and wastewater flows are allocated to individual subareas to identify current and future deficiencies in the collection system. The components of the City’s sewer system are organized into three categories for capacity evaluation: • Major Gravity Lines • Force Mains • Main Sewage Pump Stations The hydraulic model, InfoSewer developed by Innovyze (formerly MWHSoft), has been used to analyze the major gravity lines within the collection system for current conditions (2011), and future conditions for the years 2017, 2031, and buildout. For the capacity analysis for the force mains and sewage pump stations, peak wet weather flows for 2031 conditions were estimated and compared to existing pump capacity. HYDRAULIC MODEL The development of the hydraulic model is described and the assumptions used to develop the model are presented in this Chapter. The output from this model is used to evaluate the capacity of the existing collection system and to identify improvements that will be required to handle the wastewater flows. The model can be updated and maintained for use as a tool to aid in future planning and design. The hydraulic model was developed by Innovyze. Version 7.5 for Windows was designed for steady-state analysis of gravity flow and pressure flow pipe networks. Version 7.5 is capable of modeling up to 6,000 nodes and is also capable for integration with the City’s GIS mapping. This version of InfoSewer also has the capability of extended time modeling. The hydraulic model used for the 2005 Plan utilized SewerCAD. The information from this model was imported into InfoSewer and updated with the latest GIS-based sewer data. 7-2 City of Marysville November 2011 Sewer Comprehensive Plan MODEL LAYERS The hydraulic model consists of numerous layers, each of which mimics a shapefile (.shp or layer) utilized in GIS. Although the layers are not specific .shp files, they can be exported as a .shp file which can be utilized in a GIS system. The layers consist of manholes, outlet, wetwells, pipes, force mains, and pumps. In the model, each of the smaller pump stations is included as fixed discharges to downstream manholes. Six of the City’s main pump stations are included with the hydraulic model and are located on a pump layer. Flow loadings were calculated separately in an Excel spreadsheet (i.e. based on area, population, and infiltration and inflow) and then input into the model at specific designated manholes. For economy, only a portion of the total collection system is modeled. All pipelines greater than 10-inch diameter are included as well as selected 8-inch pipelines. A schematic of the skeletonized system is shown in Figure 7-1 along with the basin overlay. A larger size figure of the pipe network is presented in the jacket of the Plan. Necessary data for the model are shown in Table 7-1. TABLE 7-1 Collection System Information(1) Category Gravity Sewers Manholes Pump Stations Dimensions Length (Calculated from X and Y coordinates of manholes and Pump Stations ) Location (X and Y coordinate from City’s GIS system) Location (X and Y coordinates from City’s GIS system) Identification No.(1) Name (from City e.g., S-Line-5165) Name (from City, e.g., S-MH-3830) Name Base Elevation -- Rim Elevation Ground Elevation Depth Upstream and Downstream Invert Elevations -- Water Level Setting Size Pipe Diameter Manhole Diameter Wet Well Diameter Flow Criteria Pipe Material -- Pump Curve Vertical Datum NGVD 88 NGVD 88 NGVD 88 (1) This information was collected for the 2005 SewerCAD model and was then imported into InfoSewer in 2011. This data was verified and updated with the City’s current GIS based data. Information required to construct the original model was obtained from record drawings, linear interpolation between known inverts, survey, and pump curves. Use of each item is described below: CITY OF MARYSVILLE SEWER COMPREHENSIVE PLANFIGURE 7-1MODELED SEWER LINES LEGEND: MODELED SEWER LINESEXISTING SEWER LINES (2011)URBAN GROWTH AREA ULTIMATE PLANNING BOUNDARYSEWERED AREA (2011) SEWERED AREA OUTSIDE UGA (2011) 0 4,500 9,0002,250 Feet M:\MARYSVILLE\11447_Sewer_Comp_Plan\Figures\Fig 7-1 MODEL_SEWER11x17.mxdSCALE 1"=4500' City of Marysville 7-3 Sewer Comprehensive Plan November 2011 Record Drawings The pipeline and manhole information for the model has been obtained from the City’s GIS information. The GIS information provided by the City includes the location of the manholes, the manhole identification, pipe segment identification, and the size and lengths of pipelines. From the GIS system, the manhole identification system follows the format S-MH-# with a three or four digit number system. The City also provided record drawings for the sewer system. These record drawings have been used to verify the pipe size and lengths and to determine the manhole rim and invert elevations. The initial vertical datum NGVD 29 was used for elevations, because the majority of the City’s record drawings used this datum. However, all elevation data were converted to NAVD 88 by adding 3.67 feet to NGVD 29 datum. NAVD 88 is the current City standard. Interpolated Manholes After collecting all the information available from the record drawings in 2004, there were gaps in the information necessary for a functional model. During compilation of the last Plan, the SewerCAD model created manholes at all intersections between two gravity sewer lines that did not already have a manhole. These manholes are created for any bends in the pipe and ends of the pipe where there are clean-outs in lieu of manholes. In the majority of these cases, the upstream and downstream invert elevations were known and a constant slope was assumed in between the manholes. The length of pipe to each junction is known from the GIS system. The invert elevations of these manholes and junctions are determined by linear interpolation between the upstream and downstream manholes. Where the SewerCAD model created “new” manholes, it utilized the manhole identification format of MH-#. Numbered manholes used in the model are presented in Exhibit III. Surveyed Manholes In the 2004 model, there were also a few sections of gravity pipe where the elevations were either missing or were incorrect. These sections, including some post 2004 sewer construction projects, were surveyed and updated for the 2011 model. In some areas, the missing information was the rim and invert elevations for saddle manholes, which were most likely installed after the original construction. In these cases, key manholes upstream and downstream in these unknown sections were surveyed. Additional survey information had been used in conjunction with the as-built drawings to convert the unknown elevations on the as-builts into invert and rim elevations using the NAVD 88 datum. One significant area of the City without known elevations was the downtown area where some of the older sewers are located. The as-built drawings provided the pipeline lengths 7-4 City of Marysville November 2011 Sewer Comprehensive Plan and constructed slopes, but not elevation. Field survey in 2004 established invert elevations for these manholes. In some instances adjacent sets of “as-builts” did not match indicating “negative” pipeline slopes. Survey information had been used to correct or confirm this “as-built” information. Pump Stations For simplicity, the small pump stations are modeled as constant-discharge pumps, so that the pump stations produce a constant discharge regardless of head conditions. Only the force mains and pump curves for Marysville West, West Trunk, Soper Hill Road, Sunnyside, 88th Street, and 51st Avenue Pump Stations are included in the model at this time. A future refinement of the model may include the pump curves for the smaller pump stations and/or the results from drawdown tests for each pump station. For the modeled pump stations, three points from the station’s pump curve were originally utilized for model input in InfoSewer. However, four of the stations were changed to constant discharge pumps to ensure that the flow mimicking the lift station capacity would continue downstream (i.e. 1,250 gpm capacity resulted in 1,250 gpm being transported downstream). These lift stations include Marysville West, West Trunk, Soper Hill Rd, and Sunnyside. The remaining lift stations however, transported all flow reaching a particular pump station so that downstream pipelines were accurately modeled. BASINS The City’s collection system is organized around seven trunk sewers or basins. Within each trunk sewer area, individual subareas were identified. These subareas were established primarily around topographic areas. Altogether there are 214 subareas within City’s UGA and planning areas. Figure 7-2 presents each numbered subarea in relation to the seven basin and 11 neighborhood planning areas. The model inputs for InfoSewer originated from loading tables set up in an Excel spreadsheet (see Appendix D). The loads resulted in average sanitary flow, peak I/I flow, peak commercial flow and fixed flow. For average sanitary flows, InfoSewer applies peaking factors for identified residential load. A summary of these peaking factors based on flow is shown in Table 7-2. Lower estimated flows (such as those in Subbasins A24-5 and F-12) are subject to high peaking factors while as the flows within a basin get larger (such as those in Subbasins CE5-7 and D6-2), the peaking factor diminishes. Higher flows have lower peaking factors. Together with peak I/I, peak commercial and pumped flow, the model evaluates the impact of peak flow on the sewer collection system. The schematic, Figure 7-3, illustrates the organization of these model inputs and outputs for InfoSewer. City of Marysville 7-5 Sewer Comprehensive Plan November 2011 TABLE 7-2 Peaking Factors Average Sanitary Sewer Flow (mgd) Peak Factor for InfoSewer Model 0.04 3.7 0.1 3.6 0.2 3.4 0.3 3.2 0.4 3.1 0.5 3.0 0.7 2.9 0.9 2.8 1.2 2.7 1.5 2.6 2.0 2.4 3.0 2.3 4.5 2.1 6.0 2.0 9.0 1.9 12.0 1.8 15.0 1.7 20.0 1.6 Getchell KelloggSisco DowntownMarshall Cedarcrest Smokey Point Sunnyside East Sunnyside Lakewood Jennings Park Urban Reserve F22 (FUTURE) A24 (FUTURE) F13 (FUTURE) A16 (FUTURE) CE5-3 (FUTURE) A18 (FUTURE)A18-3 (FUTURE) CE5-7 G7 CW1 D3-5 D6-2 CW15 A6 F22-1 G3 B1 F13-1 A25-1 D3-12 A19 D10-2 G1 D10-6 A24-5 CW11-1 A21 F4 D6-5 F21 A26 F20 F12 D1 F22 D10-3 A20 F14 A23 A10A16 A7 D10-4 D3-11 A15 G2 A13 F5 D6 A25 A22 G4 G8 D10-1 F15 D3-8 D9 B2 F13 F10 D12 A24 A18 D3 A28 D5 CW3 A27 F7 D3-1 F13-2 A8 A24-4 A17 A5 CW11 CE5-2 A24-2 B3 D3-4 A24-3 D3-10 D3-9 D5-2 CE5CE7 A12 CE6 G5 CW7 D3-6 F16 F2 D3-13 CW2 F3 B5 A24-1 F17 CW14 F9 CW8 D3-3 G6 F19 D4 D6-4 A2 CE5-3 CE2 CW12 A9 A16-1 CW10 CW4 A12-2 F8 D3-7 D3-2 D2 A4 D10-5 CW6 B4 F18 F11 A1 D8 D9-1 D10 A18-1 CE5-1 A12-3 D5-1 D11 CW13 A14 D7 CE9 D6-3 A18-3 CE5-4 CW9 D7-2 CW5 A12-4 F1 CE8 CE4A12-1 F6 A18-2 CE3 A11 D6-1 CE1 D7-1 CE5-6 CE5-5 CITY OF MARYSVILLE SEWER COMPREHENSIVE PLAN FIGURE 7-2 CONSULTING ENGINEERS NEIGHBORHOOD PLANNING³LEGEND: MODELED SUB-BASINS PLAN AREAS BASINS: BASIN A BASIN B BASIN C EAST BASIN C WEST BASIN D BASIN F BASIN G 0 4,300 8,6002,150 Feet M:\MARYSVILLE\11447_Sewer_Comp_Plan\Figures/Fig 7-2 NBRHD-PLANNING.MXDSCALE 1" = 4300' 7-6 City of Marysville November 2011 Sewer Comprehensive Plan HYDRAULIC MODELING ANALYSIS Hydraulic models have been first developed for 2011, 2017, and 2031 conditions for the existing sewer collections system. This approach was used to identify any patterns, which may exist for pipeline deficiencies. Once the analyses have been completed for these conditions, an additional hydraulic model is prepared with improvements to correct pipeline deficiencies. A final hydraulic model is prepared for “build-out” conditions. Basin data for 2011, 2017, and 2031 are presented in Appendix D. Pipe deficiencies resulting from the model are included in Appendix E for 2011, 2017, and 2031. For the initial model set-up (2011), there are a total of 1,225 nodes, or manholes, in the InfoSewer format. Approximately 318,865 lineal feet of pipe is included for the hydraulic model, 27 percent of the total collection system. To support the development of the hydraulic model and to present the model results, six exhibits have been prepared. Each of these is listed below and included in jackets at the end of this Plan. Exhibit I: Existing Sewer System and Land Use Subareas Exhibit II: Sewer System Aerial Map Exhibit III: Modeled Sewer Lines, Manhole IDs, and Basins Exhibit IV: Pipe ID and Capacity Deficiencies (Model Runs 2011, 2017, and 2031) Exhibit V: Modeled Sewer Lines w/Improvements and Buildout Conditions Exhibit VI: Pipe ID and Pipeline Velocity Deficiencies (2011) YEAR 2011 HYDRAULIC MODELING ANALYSIS EXISTING POPULATION There are three requirements for identifying existing population for 2011 conditions. The first is to establish the total population for the sewer service area. The second is the population within the UGA and the third is the population currently sewered. These population numbers were developed in Chapter 3 and are summarized in Table 7-3. TABLE 7-3 2011 Population Sewer Service Area Sewered Population UGA 61,491 48,449 Non-UGA 3,178 2,094 Total 64,669 50,543 City of Marysville 7-7 Sewer Comprehensive Plan November 2011 The population numbers were developed using the land use codes assigned to individual parcels in the Snohomish County Assessor parcel database, also known as the Integrated Land Records system. These codes can be used to categorize each residential parcel into single family or multi-family housing units. Single family units were assigned 3.0 persons per household and multi-family units were assigned 2.0 persons per household per the City’s Community Development Department. The number and locations of parcels connected to sewer was determined by address matching a table of utility billing account information to the parcel data. Population not connected to the sewer system was excluded from the hydraulic model. Average residential wastewater flow for each subarea has been determined by multiplying the connected sewer population by a unit flow factor of 60 gallons per day per person. SCHOOLS Based on the City’s water records during compilation of the 2005 Plan, the average daily water use by the school system was 132,000 gpd. For the hydraulic model, a unit flow rate of 10 gpd per student was calculated using a total student/staff population of 13,339 (11,390 students based off of 2010 annual enrollment and approximately 2,000 staff). In 2011, records showed similar results. Therefore, the flow rate of 10 gpd continued to be used for the recent model. Individual school addresses have been used to locate each school and its student/staff population within the appropriate subarea. COMMERCIAL/INDUSTRIAL The basis for commercial/industrial inputs into the hydraulic model is a combination of water records and acreages used for this category. The ten largest commercial/industrial customers were identified (Table 6-5) and placed in the “fixed” category. For example, Pacific Coast Feather Co., the largest commercial/industrial user, is located in subarea F-14 and is shown as a “fixed” or pumped flow for this subarea. Based on water consumption records, the total commercial/industrial use is 513,810 gallons per day, and the 10 largest users account for 184,575 gallons per day, or 36 percent of the total. For the other commercial/industrial connections a peaked flow rate of 2,700 gallons per acre per day (gpad) was used to account for anticipated commercial and industrial development. This flow rate is based on a typical planning number. Actual water consumption resulted in 1,023 gpad (after taking out the top ten largest water consumers). A conservative approach was decided upon when selecting the 2,700 gpad commercial flow rate. The 150 gpm allowed by agreement with the Tulalip Tribes was not included in the model since the Tribes now own and operate a wastewater treatment plant. 7-8 City of Marysville November 2011 Sewer Comprehensive Plan INFILTRATION/INFLOW In Chapter 6 of the Plan, infiltration/inflow has been characterized for average, maximum month, peak day, and peak hour conditions. For the hydraulic model, the unit flow rate for the peak hour flow is used. Based on a service area of 4,979 acres and a peak hour I/I, the unit flow rate is 1,044 gallons per day per acre (i.e 5.2 MGD divided by 4,979 acres). For the model, the peak rate of 1,100 gpd/acre for the 2011 modeling scenario was selected. For the 2017 and 2031 gpad this rate has been decreased to 800 gpad to account for the assumption that deteriorating pipes are being replaced through the City’s Sewer Renewal and Replacement program within these years. YEAR 2011 HYDRAULIC MODELING DATA Appendix D summarizes the loading data required for the 2011 hydraulic model. For InfoSewer input, four loadings were used: total residential flow, commercial/industrial flow, peak infiltration/inflow, and fixed or pumped flow as shown in Figure 7-3. For each subarea the average annual sanitary flow is determined based on residential population, student/staff population, and commercial/industrial use. For the residential sanitary flow, a range of peaking factors is applied as presented in Table 7-2 whereas the commercial/industrial and I/I flows were already peaked prior to being entered into the model. Appendix E and Figure 7-4 presents the initial modeling results for 2011 conditions. The report in Appendix E identifies each pipeline segment and compares estimated peak flows with design capacity. About 50 percent of the modeled pipeline segments are characterized by low velocity (less than 2.0 feet per second). A total of 35 segments are shown to have insufficient pipeline capacity. YEAR 2017 HYDRAULIC MODELING ANALYSIS The data developed for 2011 conditions was updated for 2017 projections. The basis for these future population estimates was the overall population projection for the UGA (Table 3-7) and the neighborhood planning capacity analysis (Table 3-8). In addition, all new population was assumed to connect to the sewer system while a steady decrease in unsewered population was expected. The summary of the 2017 population is shown in Table 7-4. TABLE 7-4 2017 Population Sewer Service Area Sewered Population UGA 69,338 59,656 Non-UGA 3,278 2,594 Total 72,616 62,250 City of Marysville 7-9 Sewer Comprehensive Plan November 2011 Table 7-4 shows an increase of 15,000 sewered population for 2017 compared to 2011. Overall, the increase in sewered population is 28 percent. A percentage of 2.7% increase in population per year is applied to project future school populations. For all scenarios, the top ten commercial/industrial water users are included in the hydraulic model as “fixed” sources. The balance of the commercial/industrial is included based on acreage at a peaked flow rate of 2,700 gpad. This model assumes all available commercial/industrial is built out by 2017. This is to gain a better understanding of the City’s sewer needs for future commercial areas, specifically Lakewood and Whiskey Ridge. For the hydraulic model, the infiltration/inflow unit flow rate is 800 gpd/acre in 2017. During this modeling scenario, the acreage served is increased from 4,979 acres in 2011 to 5,708 acres in 2017. So although the unit flow rate is less than 2011, the amount of I/I in 2017 (i.e. 5,708 acres x 800 gpd/acre) increases overall due to the increase in amount of acreage being sewered. Appendix D summarizes the loading data required for each subarea for 2017 conditions, and Appendix E and Figure 7-5 presents the modeling results for 2017. For 2017, there are 31 new pipe segments with insufficient pipeline capacity. The total number, including 2011 model results, is 66. YEAR 2031 HYDRAULIC MODELING ANALYSIS Similar to the development of the 2017 loading table, the initial data developed for 2011 was also updated for 2031 conditions. The overall population projections were based on the UGA population for 2031 and the neighborhood capacity analysis. Individual subareas were assigned population based on their land use designation (single-family and multi-family) and the available land for development. The summary of the 2031 population is shown in Table 7-5. TABLE 7-5 2031 Population Sewer Service Area Sewered Population UGA 84,989 84,989 Non-UGA 3,278 3,278 Total 87,757 87,757 Overall, the increase in sewered population from 2011 to 2031 is 37,214, or 73 percent. As with the 2017 flows, a percentage of 2.7% increase in population per year is applied to project future school populations. 7-10 City of Marysville November 2011 Sewer Comprehensive Plan For all scenarios, the top ten commercial/industrial water users are included in the hydraulic model as “fixed” sources. The balance of the commercial/industrial is included based on acreage at a peaked flow rate of 2,700 gpad. This model assumes all available commercial/industrial is built out by 2017. This is to gain a better understanding of the City’s sewer needs for future commercial areas, specifically Lakewood and Whiskey Ridge. For the hydraulic model, the infiltration/inflow unit flow rate is 800 gpad in 2031. The acreage served for 2031 is 7,340 acres, a 47% increase above the amount of I/I acres used for 2011. Appendix D summarizes the loading data required for each subarea for 2031 conditions, and Appendix E and Figure 7-6 presents the modeling results for 2031. YEAR 2011, 2017, AND 2031 MODELING RESULTS WITHOUT IMPROVEMENTS Modeled peak flows are compared to projected peak flows developed in Table 6-9. As presented in Table 7-6, the modeled peak flows are much higher than projected peak flows due to the conservative approach to model the sewer system as indicated in Chapter 3. TABLE 7-6 Modeled Peak Flows vs. Projected Peak Flows Year Projected Peak Flow (mgd from Table 6-9) Modeled Peak Flow (mgd) 2010 10.7 21.7 2017 12.7 22.2 2031 16.9 23.8 The three hydraulic modeling analyses identified a total of 118 pipeline capacity deficiencies. Many other pipelines have velocities less than 2 feet per second (a deficiency criteria) but are capable of handling the existing and projected flows. Table 7- 7 summarizes these pipeline capacity deficiencies by model year and basin. City of Marysville 7-11 Sewer Comprehensive Plan November 2011 TABLE 7-7 Pipeline Capacity Deficiencies for 2011, 2017, and 2031 without Improvements Basin ID Year 2011 Additions in 2017 Additions in 2031 Total Trunk A 0 2 3 5 Trunk B 0 0 0 0 Trunk CE 7 2 8 17 Trunk CW 6 1 15 22 Trunk D 12 3 12 27 Trunk F 3 23 14 40 Trunk G 7 0 0 7 Total 35 31 52 118 Exhibit IV in the jacket of the Plan presents the locations of each of the pipe capacity deficiencies by year and basin. Of the 118 deficiencies identified, Basin F contained 40 deficient pipes. These pipes are clustered mostly into two areas. The first is located near 169th Pl. NE and 27th Ave. NE in the Lakewood area and consists of mostly 12-inch diameter pipes constructed at flat grades. The second area lies along State Ave. between 124th St. NE and 136th St. NE. with 18-inch and 21-inch diameter pipes that have minimal grade. This area will be relieved with the addition of the Lakewood Sewer Extension Project Phase II which would extend a new 36-inch pipe east along 136th St., diverting Lakewood flows to Trunk A. The Trunk D Basin had the second highest number of pipeline deficiencies with 27. These deficiencies are scattered mostly over the northwest corner of the basin, along 70th St. NE. These pipes are generally the result of pipelines constructed at flat grades. Two pipelines, S-LINE-716 and S-LINE-712, have reverse or very flat grades. Basin D3-11 also contained a few deficient pipes along 75th Ave. NE. This is a relatively newer area, constructed in the 1990’s with 8-inch PVC pipes. Very minimal surcharging resulted from the model for this area. The Trunk CW Basin has the third highest number of pipeline deficiencies with 22. The deficiencies are scattered all throughout the basin but the majority lie between 1st St. and Grove St. in the older downtown portion of the City. Most of these pipes are 18-inch diameter. At 1st St. they become 21-inch and 24-inch diameter pipes. Many of these pipes were installed over 50 years ago and have relatively flat slopes. As with Basin F, this area will benefit by diverting future Lakewood flows east along 136th St. NE toward Trunk A. 7-12 City of Marysville November 2011 Sewer Comprehensive Plan The Trunk CE Basin has a total of 17 pipeline deficiencies primarily located along 88th Street. The most significant deficiencies are sections of 12-inch pipe in the vicinity of 88th Street east of 51st Dr. NE based on 2031 conditions. The Trunk G Basin contained 7 pipes that were found to not have capacity in 2031. All of these pipes are located along Beach Ave. and 1st St. This deficiency was previously identified as a capital project in the 2005 Comprehensive Plan. The Trunk A Basin has a total of 5 pipe capacity deficiencies. The deficiencies begin to occur in 2017. A segment of 8-inch pipe along 80th St. NE near 52nd Dr. NE was constructed at a flat slope. A second deficiency was identified along 122nd Pl. NE and 51st Ave. NE for a 21-inch diameter pipe yet this area was not considered deficient in 2011 or 2017. The third deficiency is located along 51st Ave. NE near 142nd Pl. NE and is a segment of a 30-inch pipe constructed with a slope of zero. No pipe capacity deficiencies were identified in the Trunk B Basin. The hydraulic model determines pipeline capacity deficiencies by comparing design capacity with total projected flow in isolated, individual pipe segments. This evaluation, however, is not complete until a surcharge analysis is prepared. A surcharge analysis considers both upstream and downstream conditions to establish a hydraulic grade line. A surcharge analysis will first determine if a surcharge exists at a manhole and then the level of the water surface under peak flow conditions. A surcharge pipeline can be a priority due to the potential for backups into residential or commercial services. The surcharge analyses were based on 2011, 2017, and 2031 flow conditions. Two pipeline segments illustrate the importance of the surcharge analysis. One is S- LINE-4849 which is a 14-inch-diameter pipe located at 172nd St. NE just west of 51st Ave. NE. Because of zero slope, the model calculates zero design capacity and identifies this pipeline as a deficiency. Yet when the surcharge analysis is prepared, the results are that there are no surcharge conditions upstream of the pipe through 2031 due to the steeper hydraulic grade line. Another pipeline is S-LINE-711, an 18-inch concrete pipe with a constructed slope of 0.001 located near the intersection of 57th Dr. NE and 70th St. NE. The model results shows a capacity deficiency since the calculated design capacity is only 1,488 gpm and the modeled flow exceeds 1,768 gpm in 2031. Yet the surcharge analysis only shows a surcharge of 0.1 feet (1 inch). Figures 7-4 through 7-6 located in Appendix E graphically present the modeling results for 2011, 2017 and 2031. The maps show the pipeline deficiencies with associated surcharged manholes. Appendix E lists the depth of surcharge associated with the deficient pipelines. Of the 142 pipeline capacity deficiencies in 2031, 104 of them have surcharges in at least one of the model years greater than 0.5’ above the top of the pipe. Many of these are minimized or deleted with the diversion of flow from Trunk F to Trunk A along 136th St. NE. City of Marysville 7-13 Sewer Comprehensive Plan November 2011 Some of the surcharged pipelines are scheduled for CIP improvements and the remainder are identified as potential areas for the City staff to observe in future years since many of these manholes showed a surcharge depth of less than 0.5’ and are not anticipated to cause a problem to neighboring properties. Numerous deficiencies are due to flat grades. YEAR 2011, 2017, AND 2031 MODELING RESULTS WITH IMPROVEMENTS Figure 7-6 shows surcharge conditions for 118 pipelines identified with capacity deficiencies. A large majority of the surcharge conditions, are identified with Trunk F. Each of these pipelines is 10- or 12-inch PVC constructed at minimum grade, or less. While these pipelines are adequate for current conditions, the results of the hydraulic model for 2017 and 2031 show that these pipelines exceed their capacity and surcharge. Increasing the diameter of these pipelines from 18- to 24-inch is one approach to eliminating pipeline surcharges in this area of the collection system. Another approach is to direct future flows to the planned Lakewood Sewer Extension Project (Phase II). This approach, as shown for build-out modeling conditions, will eliminate each of these deficiencies in Trunk F. With many of the surcharge conditions eliminated with the Lakewood Sewer Extension Project, there are a few remaining surcharged pipelines. These areas are included in Basins CW1, CE5-3, CE5, D3, D6-1 and F21. Each of the improvements for these basins are described below. In Basin CW1, this area includes some of the City’s oldest pipelines. The model demonstrated pipes that were under capacity along Columbia Ave. and west along 1st St. Improvements here include replacement of approximately 615 lf of 21-inch sewer with 24-inch gravity sewer. In addition, the 580 LF of 24-inch pipe downstream of the existing 21-inch pipeline shall be replaced to a more consistent slope of 0.0029. In Basin CE5-3, the pipe in 89th Pl. NE showed a substantial amount of minor surcharging within the model amongst the 12-inch concrete pipes located in this area. Improvements to the pipes would include rehabilitation with a cured-in-place liner for a distance of approximately 2,170 lineal feet between manholes S-MH-1993 and S-MH- 1665. Along 88th St NE, in Basin CE5, surcharging resulted in the existing 12-inch pipes along this area. Improvements would include increasing the pipe size from 12-inch diameter pipes to 15-inch diameter pipes for a distance of approximately 1,020 lineal feet between manhole S-MH-4608 to S-MH-1665. City staff recognizes that this area is prone to sags in the pipe. The City intends to construct this project in conjunction with any future road related projects. 7-14 City of Marysville November 2011 Sewer Comprehensive Plan Along Sunnyside Blvd. from 53rd Ave. NE to 60th Dr. NE (Basin D3), the hydraulic model demonstrated surcharging results. Improvements in this area would include replacing approximately 2,750 lineal feet of existing 24-inch pipe to 30-inch between manhole S-MH-624 to S-MH-3608. At 64th Avenue and approximately 71st Street (Basin D6-1), an existing 18-inch sewer is connected to a 12-inch sewer. The 2031 results for the hydraulic model showed surcharging for 508 linear feet of 12-inch sewer between manholes S-MH-702 and S- MH-733. To ensure future capacity, these two pipe segments should be upsized to 18- inch. The model showed significant surcharging occurring during 2031 along 169th Pl. NE extending up north along 277th Ave and Spring Lane Ave. (Basin F21). The recommended project in this area would be to replace the current 10-inch and 12-inch pipes with 15-inch pipes for approximately 3,035 lineal feet. However, future development could be directed south toward an existing 15-inch stub located on 164th Pl. NE which would thereby allow additional capacity to the north. Each of the summary sheets for 2011, 2017 and 2031, presented in Appendix E, lists each surcharged pipeline. Exhibit V in the back of the Plan shows the planned improvement to correct these deficiencies. BUILDOUT HYDRAULIC MODELING ANALYSIS Buildout conditions for the City’s UGA will occur near 2031. The projected population within the UGA for 2031 is 84,989 while the holding capacity is 88,032, a difference of about 3,000. For buildout conditions for the City’s sewer system, both the current UGA and planning areas located outside of the UGA must be considered. There are a total of five planning areas as presented in Figure 2-2. Population estimates for each of these areas are presented in Table 3-12 and the summary of buildout population is shown in Table 7-8. City of Marysville 7-15 Sewer Comprehensive Plan November 2011 TABLE 7-8 Buildout Population Sewer Service Area Sewered Population UGA 88,032 NON-UGA 3,278 Sub Total 91,310 Planning Areas #3, #4, #6 56,694 Sub Total 148,004 Planning Areas #1 and #2 11,571 Total 159,575 To model buildout conditions for Planning Areas #3, #4, and #5 (the Lakewood area), planned CIP improvements and a preliminary layout of the expanded collection system were prepared. This layout is included in Exhibit V in the jacket of the Plan. The layout includes three future pump stations, one sized for 2,800 gpm, another for 3,600 gpm, and one smaller station for 300 gpm. Similarly, a preliminary layout was prepared for the East Sunnyside area. The layout includes preliminary pipeline sizes and one future pump station sized for 200 gpm. This layout is also included in Exhibit V in the jacket of the Plan. Appendix E and Figure 7-7 presents a summary of the modeling results for buildout conditions. BUILDOUT MODELING RESULTS With the buildout populations for the planning areas and UGA, the modeled peak flow increases from approximately 23.8 mgd in 2031to 25.6 mgd. This additional peak flow is primarily confined to impacts on Trunks A and CE. The pipeline capacity deficiencies are shown on Figure 7-7 along with the results of the surcharge analysis. The hydraulic model results for buildout conditions are based on the assumption that planned CIP improvements are completed. The most significant improvement is the extension of the Lakewood Sewer Extension Project from State Street to Trunk A, For buildout conditions, a 36-inch sewer should be constructed along 136th Street to connect to Trunk A. The Lakewood Sewer Extension Project and other CIP improvements are shown on Exhibit V in the pocket of the Plan. The primary impact to Trunk A is confined to 51st Avenue from 126th Pl. NE to approximately 148th Street, 116th St. NE and approximately 102nd Pl. NE. Five pipelines have capacity deficiencies along 51st Ave., mostly due to fairly flat grades. The surcharging along 51st Ave.is a result of the upstream Lakewood Sewer Extension connection. The model also revealed significant surcharging at the input points along 7-16 City of Marysville November 2011 Sewer Comprehensive Plan 116th St. NE (manhole S-MH-4739) and 109th St.NE (S-MH-3789). In the future, the flow from the planning areas may be more disbursed into the existing pipe network then what is represented by the skeletonized hydraulic model and therefore, the pipes within these areas may not present a problem. Individual subbasin analyzes shall be conducted prior to specific developments occurring within the planning areas. The locations of the buildout pipe deficiencies are presented in Exhibit V. For Trunk CE, 17 pipelines have capacity deficiencies under buildout conditions. Most of the capacity issues exist with the 18-inch pipes lying just west of 60th Dr. NE. Details and figures of each pipeline capacity, deficiency and surcharge analysis are included in Appendix E. OTHER PIPELINE DEFICIENCIES The hydraulic model can provide some, but not all, information about current pipeline deficiencies. Where “sagging” has occurred, offset joints developed, or manholes have been improperly installed, the hydraulic model most likely will not reflect these problems. City staff has identified a few other problem areas which were not shown by the results of the hydraulic model or are not already included with the City’s CIP. Several noted problem areas were associated with minimum pipeline grades and therefore, require frequent pipe cleaning. These areas are addressed in a separate memorandum to the City and will continue to be assessed throughout future years. PUMP STATION CAPACITY ANALYSIS The City operates and maintains 15 pump stations. Several of the City’s pump stations can be considered “developer-type” stations with limited service area. The City’s primary pump stations, and ones which are included as part of the hydraulic model, are Marysville West, 88th Street, 51st Avenue, Soper Hill, Sunnyside, and West Trunk. For the pump station capacity analysis, the smaller pump stations were analyzed based on available “as-built” information and other land use information. The primary information was the number of single family lots served by the pump station and the estimated area with the pump station service area. Together, this information was used to estimate buildout peak flows. Table 7-9 presents the capacity evaluation for the small pump stations. The “developer type” pump stations all have sufficient, or surplus capacity. Generally, the City standards result in more than adequate pump station capacity. For the City’s main pump stations, the results of the hydraulic model estimated peak flows for 2017 and 2031 conditions. These peak flows are compared to each of the pump City of Marysville 7-17 Sewer Comprehensive Plan November 2011 station’s existing capacity in Table 7-10. For both 2017 and 2031, capacity surplus or deficiency is determined. The results of Table 7-10 show that each of the City’s main pump stations have adequate capacity through 2017 except for the West Trunk Pump Station. The rated pump station capacity is based on the assumption that the third pump is out of service. Current records indicate that one pump tends to pump between 1,500 gpm to 1,800 gpm and two pumps tend to pump 2,800 gpm. As flow increases in the region, the pumps can be upsized to allow for the additional 1,800 gpm increase anticipated to flow to the station by 2031. The Soper Hill Pump Station No. 11 and the 51st St. Pump Station No. 6 also appear to be undersized by 2031. The Soper Hill is just barely out of capacity by 33 gpm and the 51st St. Station is estimated to be undersized by approximately 700 gpm. RECOMMENDED PUMP STATION IMPROVEMENTS The West Trunk pump station will reach its rated capacity of 3,300 gpm prior to 2017. Upsizing of the pumps to meet future peak flow demands is being analyzed, and money has been allocated in the 6 year CIP to make the needed improvements. Installation of emergency generators at two of the city’s pump stations are included in the 6 year CIP. The generator installation at Carroll’s Creek pump station is scheduled for 2016 and the generator installation at Cedarcrest Vista pump station is scheduled for 2017. Construction of the new Whiskey Ridge Sewer Pump Station and force main is included in the 6 year CIP and is estimated to be constructed in 2014. A purchase agreement for the Marysville West Pump Station is currently being negotiated between the City of Marysville and the Tulalip Tribes. Purchase of the pump station by the Tribes is anticipated to take place in the near future, therefore, no upgrades to the station are being considered at this time. Although flow projections show both the 51st Street pump station and the Soper Hill pump station being undersized by year 2031, they meet projections through 2017, so no improvements are schedule for either of those during this 6 year CIP. City of Marysville 7-18 Sewer Comprehensive Plan November 2011 TABLE 7-9 “Developer-Type” Pump Station Capacity Analysis Pump Station ID No. of Existing Single Family Lots Single Family Population Average Sanitary Flow (gpd) Peak(1) Sanitary Flow (gpd) Est.(2) Peak I/I (gpd) Total Peak Flow (gpm) Pump Station Capacity (gpm) Surplus (+)/ Def (-) (gpm) Carrol’s Creek, Station No. 7 288 864 51,840 207,360 58,000 184 400 +216 Regan Road(3) Station No. 9 -- 8,610 34,440 11,950 32 122 +90 3rd St. Pump Station 4 12 720 2,880 2,750 4 200 +196 Ash Ave. Pump Station 8 24 1,440 5,760 2,530 6 200 +194 Kellogg Ridge 67 201 12,060 48,240 10,000 40 400 +360 Quilceda Glen(4) 33 99 5,940 23,760 3,560 19 250 +231 Cedar Crest 148 444 26,640 106,560 9,000 80 450 +370 Eagle Bay 12 36 2,160 8,640 2,200 8 850 +842 Waterfront Park(5) -- 300 1,200 5,500 5 57 +52 (1) For small pump stations, a peaking factor of 4 is utilized. (2) Estimated peak I/I is based on acreage served times 1,100 gpad. (3) Based on 50 percent of estimated flows for subarea A1. (4) Only 13 lots in plat. Estimate includes potential for an additional 20 lots from adjacent vacant property. (5) Designed for 57 gpm capacity to serve park restroom and facilities. City of Marysville 7-19 Sewer Comprehensive Plan November 2011 TABLE 7-10 Main Pump Station Capacity Analysis Pump Station ID Pump Station Capacity (gpm) Estimated Peak Flow (gpm) Capacity Surplus (+) or Deficit (-) 2017 2031 2017 2031 Soper Hill Station No. 11 550 (1,160 rpm), 1,250 (1,750 rpm) 783 1,283 +467 -33 88th Street(1) Pump Station, Station No. 2 500 142 313 +358 +187 Marysville West Pump Station, Station No. 5 1,150 295 358 +855 +792 51st Street Pump Station, Station No. 6 6,500 (1,160 rpm) 6,380 7,207 +120 -707 Sunnyside Pump Station, Station No. 3 1,780 1,570 1,643 +210 +137 West Trunk Pump Station 3,300 4,490 5,112 -1190 -1812 (1) Estimated peak flow is based on 2,700 gpad for commercial flows, an I/I rate of acreage served times 800 gpad, and a weighted peaking factor on residential flow times 60 gal/capita/day. City of Marysville 7-20 Sewer Comprehensive Plan November 2011 FORCE MAIN CAPACITY EVALUATION The capacity evaluation for the City’s force mains is tied directly to the pump station capacity evaluation. The capacity of each force main is based on a maximum design velocity of 8 feet per second (fps). This capacity is compared to the existing pump station capacity and the predicted peak flow at the year 2031. The results of this evaluation are shown in Table 7-11. As seen in Table 7-11, both the 51st Avenue Pump Station force main and the West Trunk force main exceed capacity by 2031. Both force mains exceed their capacity by approximately 2%. As these areas develop, the City may want to evaluate these force mains in greater detail to ensure capacity is provided by 2031. Of the smaller developer type, pump stations, both Cedar Crest Vista and Kellogg Ridge have 4-inch force mains with pipeline velocities in excess of 8 fps. Both pump stations appear to have pump capacities well beyond the peak flow requirements. These velocities of 10 - 11 fps are not considered serious enough deficiencies to warrant replacement with larger pipe diameters. City of Marysville 7-21 Sewer Comprehensive Plan November 2011 TABLE 7-11 Force Main Capacity Evaluation Pump Station (Force Main Source) Pump Station Capacity gpm Force Main Diameter inches Existing(1) Capacity (gpm) Peak Flow Requirement (gpm) Soper Hill 1,250 10 1,957 1,283 Carrol’s Creek Landing 400 6 705 184 88th Street 500 10 1,957 313 Regan Road 122 4 313 32 Marysville West 1,150 14 3,838 358 Cedar Crest Vista 450 4 313 32 51st Avenue 6,500 20 7,037 7,207 Sunnyside 1,780 12 2,820 1,643 3rd St. Station 200 8 1,253 4 Kellogg Ridge 400 4 313 40 Quilceda Glen 250 4 313 19 Ash Avenue 200 4 313 6 Cedar Crest 450 4 313 80 Eagle Bay 850 4 313 8 Waterfront Park 57 2.5 122 5 West Trunk 3,300 16 5,010 5,112 To Everett SEP 14,100 36 25,377 16,535 To Everett SEP 14,100 2-26 22,558 16,535 (1) Based on pipeline velocity of 8 fps. (2) Numbers shown in bold represent a capacity that is anticipated to be exceeded in 2031. 7-22 City of Marysville September 2011 Draft Sewer Comprehensive Plan SUMMARY OF COLLECTION SYSTEM IMPROVEMENTS Proposed improvements can be characterized as projects to correct current deficiencies or ones to accommodate future growth. The first priority is to address any current pipeline and pump station deficiencies. The results of the hydraulic model for 2011 indicated 35 pipeline capacity deficiencies with mostly minimal surcharge issues. The one exception is the area near Columbia and 1st St. which identified an extensive backwater effect due to undersized pipes along 1st St. Many deficiencies in the 2011 scenario can be attributed to flat or minimally sloped pipes. Two deficiencies were either confirmed or identified by survey in the previous 2005 Plan. One problem area is located near the intersection of Grove and 67th Streets. Two short pipeline segments have negative to flat slope. Another problem area, located at 43rd Avenue and 123rd Place, is backflow caused by incorrect manhole installation. The outlet of S-MH-2382 was installed 4 inches higher than the inlet. Both areas will be monitored in the future to observe whether these pipes provide concern in terms of backwater effects. Depending on the extent of new development, the Lakewood Sewer will need to be connected to Trunk A to alleviate a number of surcharged pipes along State Ave. This extension includes a 36-inch diameter pipeline along 136th Street to Trunk A at 51st Avenue and is shown to be constructed in 2018. This project is presented on Exhibit V. The most serious deficiencies with the collection system are low velocity pipelines (<2.0 fps). Of the 318,865 lf of pipeline modeled, approximately 50 percent of the pipelines were found to have low velocities. Most of these pipelines were large enough in diameter to provide sufficient capacity. However, these low velocity pipelines will collect grease and inert material and require more frequent cleaning and flushing than pipelines with velocity greater than 2 fps. Exhibit VI show the location of the low velocity pipelines, which were part of the hydraulic model. As noted in the 2005 Plan, there are several areas of the collection system, which are recommended for further study. The limited data from the 2004 flow monitoring showed above normal infiltration/inflow for Trunk CE and the as-built drawings present very flat grades for part of the 18-inch sewer. Trunk CE should include additional flow monitoring and TV inspection to better assess any potential problems. The Trunk D Basin contains one of the fastest developing areas of the City, where several pipelines are shown to surcharge in 2017 and beyond. Better flow characterization along Sunnyside Road near the 3rd St. Pump Station, and along 70th Street would allow refinements to the hydraulic model, particularly regarding the level of infiltration/inflow. Most of the City’s pump stations have adequate capacity through 2031. The three exceptions include the West Trunk pump station, the 51st Street pump station, and the Soper Hill pump station, where capacity deficits reach 1812, 707, and 33 gpm City of Marysville 7-23 Sewer Comprehensive Plan November 2011 respectively in 2031. The deficiencies can be corrected by upsizing pumps at the stations. The West Trunk pump station shows a deficiency of 1190 gpm in 2017, therefore it has been included in the 6 year CIP for pump upsizing improvements in order to maintain sufficient capacity at the station. The 51st Street pump station shows a deficiency of 707 gpm capacity in 2031 and will be monitored in the future to ensure adequate capacity is maintained. The Soper Hill Station shows a small deficiency of 33 gpm capacity in 2031 and will be monitored in the future to ensure adequate capacity can be provided. Table 7-12 provides a list of the capital improvement projects for the collection system and pump stations. Project costs and descriptions are included in Chapter 11. TABLE 7-12 Collection System and Pump Station Capital Improvement Projects ID Description Construction Year Sanitary Sewer Mains SS-A Sewer Main Oversizing 2012 thru 2017 SS-B Renewals and Replacements 2013 thru 2017 SS-C Whiskey Ridge Sewer Extension 2012 SS-D 71st St NE Sewer Upsizing - 64th Ave NE to 66th Ave NE 2015 SS-E Trunk G Rehabilitation – Cedar to Columbia 2016 - Lakewood Sewer Extension Project – Phase 2 2018 - 88th St NE at Allen Creek 2022 - Sunnyside Blvd from 53rd Ave. NE to 60th Dr. NE 2024 - 169th Pl. NE and 277th Pl. NE 2026 - 152nd Trunk (51st to the East) 2028 Pump Stations PS-A Whiskey Ridge Sewer Pump Station and Force Main 2012 thru 2014 PS-B West Trunk Pump Station – Upsizing Pumps 2013 PS-C Carroll’s Creek Pump Station – Emergency Generator 2016 PS-D Cedarcrest Vista Pump Station – Emergency Generator 2017 - 51st St. Pump Station – Upsizing Pumps 2025 - Soper Hill Pump Station – Upsizing Pumps 2030 City of Marysville 8-1 Sewer Comprehensive Plan November 2011 CHAPTER 8 WASTEWATER TREATMENT PLANT ANALYSIS INTRODUCTION The purpose of this Chapter is to evaluate the wastewater treatment plant (WWTP) for its ability to meet its treatment objectives based on projected future flow and loadings. The projected flow and loading rates for the planning period 2010 to 2031 were developed in Chapter 6 (Tables 6-9 and 6-10). The treatment plant effluent quality must meet the requirements in the existing and future NPDES permits for CBOD5, TSS, fecal coliform, and pH. The existing permit conditions are presented in Tables 5-6 and 5-7 for both low and high-river flow conditions. The loading limits shown in these tables are likely to remain the same upon issuance of the City’s new permit in 2011/2012. The concentration limits should also remain unchanged and are presented in Table 8-1. These limits serve as the basis for the performance evaluation for the liquid stream processes. The hydraulic capacity of the WWTP is also evaluated at the projected peak hour flow. The Phase 2 upgrade work that was completed in 2004, included new effluent pumps and a pipeline to discharge treated effluent to the City of Everett and the Deep Marine Outfall. Use of this marine discharge during low flow periods avoids the TMDL limits established for the Snohomish River and the Steamboat Slough Outfall. These limits include a seasonal limit on ammonia of 178 lbs/day on a monthly average. (Table 5-6). The current lagoon treatment system was not designed to achieve this limit. Instead, WWTP effluent is discharged to the deepwater outfall from July through October to avoid the need for ammonia removal. As a result of this outfall discharge, ammonia removal is not evaluated in this Chapter. This Chapter also evaluates the potential for water reclamation and reuse. TABLE 8-1 NPDES Effluent Concentration Limitations Parameter Average Monthly Average Weekly Maximum Daily CBOD5 25 mg/L(1) 40 mg/L N/A TSS 30 mg/L(1) 45 mg/L N/A pH N/A N/A 6.0 to 9.0 Fecal Coliform 200 cfu/100 ml 400 cfu/100 ml N/A (1) Or 15 percent of the respective monthly average influent concentrations, whichever is more stringent. 8-2 City of Marysville November 2011 Sewer Comprehensive Plan CAPACITY EVALUATION AT DESIGN FLOWS AND LOADINGS Table 8-2 presents a comparison of the WWTP capacity upon completion of Phase 2 work with the projected flows and loading developed in Chapter 6. TABLE 8-2 Comparison of Phase 2 Capacity Rating to Current and Projected WWTP Flows and Loadings Parameter Phase 2 Design Criteria(1) 2010 (2) 2017 Projection(2) 2031 Projection(2) Average Annual Flow (mgd) 10.1 4.7 5.8 8.2 Maximum Month Flow (mgd) 12.7 6.1 7.6 11.3 Peak Hour (mgd) 20.3 10.7 12.7 16.9 Average Annual BOD5 Loading (lbs/day) 17,070 10,419 12,846 18,110 Maximum Month BOD5 Loading (lbs/day) 20,143 13,812 16,997 23,963 Average Annual TSS Loading (lbs/day) 17,815 10,029 12,365 17,432 Maximum Month TSS Loading (lbs/day) 24,229 14,356 17,689 24,939 (1) Drawing G-5, WWTP Upgrade and Expansion - Phase 2, Tetratech/KCM, Inc. (May 2003) (2) Tables 6-9 and 6-10 of this Plan. The following sections evaluate the capacity requirements of major WWTP components at 2017 and 2031 projected flow and loadings. The five major WWTP’s components evaluated are the headworks, aeration system (lagoons), effluent filtration, disinfection, and effluent disposal. Figure 8-1 presents each of these components as part of the WWTP hydraulic profile. Where applicable, system components are compared to accepted design criteria, such as published in the Washington State Department of Ecology Criteria for Sewage Works Design (Orange Book, 1998), WEF Manual of Practice No. 8 (MOP 8, 1998), and Metcalf & Eddy Wastewater Engineering (4th Edition, 2003). HEADWORKS INFLUENT SCREW LIFT PUMPS Influent wastewater from Trunk A is discharged to three screw pumps, each with a capacity of 6,215 gpm, or 8.95 mgd. Ecology Orange Book reliability requirements state that pumping stations must be capable of pumping the peak flow with the largest unit out of service. Peak day influent flow in 2031 is forecasted at 16.9 mgd, and less than the City of Marysville 8-3 Sewer Comprehensive Plan November 2011 pumping capacity of 17.9 mgd with one unit out of service, therefore the screw pumps are considered adequate for peak day flow through the year 2031. INFLUENT SCREENING The headworks includes two mechanical bar screens each with a rated capacity of 13.7 mgd. There is also a manual bar screen in a bypass channel. Ecology’s Orange Book requires that influent screening be provided to handle the peak hour flow and that a bypass screen be available for the peak hour flow. With both mechanical screens in operation, the capacity is 27.4 mgd, which is greater than the peak hour flow of 16.9 mgd projected for 2031. Therefore, the screens are adequate for peak flow conditions. The mechanically cleaned screens have a 1 1/2-inch bar spacing, which allows a significant amount of plastics and other debris to pass into downstream processes. One option that has been considered, is to retrofit the screens with 3/8-inch bar spacing to remove more inert material and prevent this material from reaching the lagoons. INFLUENT FLOW MEASUREMENT Influent flow measurement is measured with a 30-inch Parshall flume. A flume with this dimension has a range of flow measurement of 0.5 to 27 mgd. The peak flow capacity exceeds the projected peak hour flow of 16.9 mgd in 2031, and therefore the flume is adequate for peak flow conditions. Some repairs to the existing concrete parshall flume structure are necessary in the future to obtain more accurate combined flows. LAGOON SYSTEM As part of the 2004 Phase 2 construction, the aerated lagoon system was expanded from four to six complete mix cells. Each cell contains five 15-hp, high speed, surface aerators and four 15-hp surface aspirating aerators. Following completion of the 2004 upgrades and issuance of the city’s new NPDES Permit in June of 2005, it became a requirement that all effluent flow be filtered prior to discharge. Filtering all of the effluent removes a greater percentage of the algae, and therefore has proven to more efficient at removing more of the effluent CBOD5. For current flows and loadings, and future flows and loadings through the next six year comprehensive planning period, concentrations indicate effluent CBOD5 less than the NPDES permit limit of 25 mg/L. Actual effluent concentrations from 2006 through 2010 averaged 9 mg/L in summer and 10 mg/L in winter. Trend line charts for Effluent CBOD5 and TSS (Appendix F) are showing a decreasing trend in both CBOD5 and TSS for the period of 2006 through 2010. Although the city realizes that downward trends are not likely in future years, upward trends appear to be happening more slowly than past projections had indicated. This is attributed to better customer awareness of water use efficiency standards, and more purchases of water 8-4 City of Marysville November 2011 Sewer Comprehensive Plan efficient appliances and devices, which maintains lower flows to the wastewater plant. The lower flows to the plant will maintain lagoon detention times for a much longer period of time into the future, thereby delaying the time before additional aerated cells need to be installed to compensate for higher flows and loadings. Because of the uncertainty associated with the predicted results in the 2005 sewer comprehensive plan, several steps were recommended in the plan to better assess the lagoons and wastewater treatment plant performance. These steps are listed below. • Conduct a study of CBOD5 concentrations at additional points in the process to improve understanding of lagoon and filter performance. The recommended points were at the WWTP influent, the last aeration cell, effluent from oxidation pond #2, final pond effluent, and filtered effluent. It was recommended that CBOD5, soluble CBOD5, and TSS be measured at each point. (Since the 2005 sewer comp plan, this has been done, and continues to be done on a bi-monthly basis). • Consider removing the south oxidation ponds from service in the summer when algae growth rates are highest. This bypass may require installation of new pipes. (No progress has been made since the 2005 comp plan to assess this operational strategy). In the 2005 sewer comprehensive plan, conditions were also evaluated with the addition of aerated cells #7 and #8. With eight aerated lagoons, predicted effluent CBOD5 concentrations were substantially reduced, and the effluent filters would reliably meet the effluent CBOD5 limits into the future. As indicated above, due to slower than predicted flow increases, aerated cells #7 and #8 will be constructed well into the future and are not included in the City’s CIP for this comprehensive plan. EFFLUENT FILTRATION The effluent filter system is a continuous upflow monomedia (sand) type with a total surface area of 2,400 square feet. The filter hydraulic loading rate varies based on the design flow basis. For maximum monthly flow, the rate is 3.0 gpm/ft2; for maximum daily flow the rate is 4.0 gpm/ft2. Metcalf & Eddy lists a filter loading rate of 5.0 gpm/ft2 for these type of filters so both rates are within accepted design criteria. Based on past calculations of 3.0 gpm/ft2, the effluent filter system has a capacity of 10.4 mgd, which exceeds the filter loading rate for the projected maximum monthly flow of 7.60 mgd in 2017. At 4.0 gpm/ft2, the capacity is 13.8 mgd which meets the projected maximum monthly flow in 2031 of 11.3 mgd. Although the calculations show that the filters are adequate through the 20 year planning period, operators of the plant have experienced difficulty getting good TSS reductions through the filters when flows near 10 mgd. Installation of additional sand filters, or some other alternative filtering system, may be necessary in the near future to accommodate higher winter time flows. City of Marysville 8-5 Sewer Comprehensive Plan November 2011 The system includes two 720 gpm pumps at 5 hp each to handle filter reject water flow. The estimated reject water flow was 512 gpm, but has proven to be closer to 750 gpm. Both pumps must run to keep up with the reject flow. An additional pump was purchased as a spare, for back up to this station, but upsizing of the pumps and/or wet well needs to be considered in the not too distant future, and is included as part of the 6 year CIP. In addition to the reject pumps, there is also a hypochlorite system in place to reduce the amount of algae recycled back to the ponds. The coagulant used for effluent filtration is alum at a design dose of 100 mg/L. At the projected maximum monthly flow of 11.3 mgd in 2031, the WWTP will use about 9,674 lbs/day of alum. 11.3 mgd x 100 mg/L alum x 8.34 = 9,674 lbs/day At a density of 80 lbs/ft3 for liquid alum, the coagulant feed system will need to supply 900 gallons per day of alum at maximum month flow. The chemical metering system includes three metering pumps, each sized at 600 gpd and three storage tanks sized at 2,500 gallons. Total storage, therefore, is 7,500 gallons. The chemical metering pumps are capable of meeting maximum month demand with one pump out of service. However, the storage capacity under 2031 maximum month conditions is only 6.6 days. Thirty day storage is desirable but with a reliable supplier less storage is acceptable. Alum is currently delivered to the plant every week to two weeks, depending on flows, with a two to three day order time. By 2031, the city may need to add at least one additional 2,500 gallon storage tank for alum to increase storage capacity. According to the manufacturing representative, the life of an alum tank is approximately 20 years. Two of the existing alum tanks were installed during the 1994 upgrades and the third tank was installed during the 2004 upgrades. DISINFECTION The WWTP has two methods available for disinfection. One, UV disinfection, is the primary disinfection method and is designed to treat a maximum monthly flow of 12.7 mgd. This UV system by Infilco Degremont is a vertically oriented arrangement installed in two channels. Each channel contains six Aquaray 40 units with 40 low-pressure, high intensity lamps each. With both channels, the system has a maximum of 480 lamps for use. The UV system is controlled to increase its dose based on higher flows and reduced transmittance. A single Allen Bradley 1200 screen monitors the operation of the UV system. The capacity of the UV system exceeds the 2031 projected maximum monthly flow of 11.3 mgd and therefore is adequate for the planning period of 20 years. The chlorine contact tank and hypochlorite system serve as a reserve disinfection system. The chlorine contact tank of 175,000 gallons provides sufficient capacity for 4.2 mgd at 8-6 City of Marysville November 2011 Sewer Comprehensive Plan the recommended contact time of 60 minutes. At a flow of 12.7 mgd, the contact time is 20 minutes, or less than the Orange Book recommendations. In addition to providing a reserve method of disinfection, the existing hypochlorite system is also utilized to maintain a chlorine residual of 0.1 mg/L for discharge to the City of Everett’s South Effluent Pump Station (SEPS). This requirement of the interlocal agreement with Everett is presented in Appendix B. EFFLUENT DISPOSAL The City’s WWTP utilizes two outfalls for effluent disposal. One is a deepwater outfall in Puget Sound owned by Kimberly Clark. This marine outfall to Puget Sound is used primarily during low river flow conditions in Steamboat Slough. Effluent conveyance facilities used for this outfall system include an effluent pump station with four 4,700 gpm pumps, a 36-inch HDPE pipeline crossing under Ebey, Steamboat, and Union Sloughs, twin 26-inch HDPE pipes to the South Everett Pump Station, and a 30-inch magnetic flow meter. The other means for effluent disposal includes a 28-inch HDPE pipeline to an outfall in Steamboat Slough with a 20-inch magnetic flow meter. This outfall is used during high river flow conditions. Ecology Orange Book reliability requirements state that pumping stations must be capable of pumping peak flow with the largest unit out of service. Peak pumping capacity with three of the four effluent pumps is 20.3 mgd, which exceeds the projected peak flow of 16.9 mgd in 2031. Pipeline velocity at peak flow in the twin 26-inch pipelines (OD) to Everett would be an estimated 5 feet per second. For the single 28-inch pipe (OD) to Steamboat Slough, the pipeline velocity at peak flow would be approximately 8 fps. Since the velocities in both pipeline systems are below the maximum design value of 10 fps, these pipeline velocities are acceptable. City of Marysville 8-7 Sewer Comprehensive Plan November 2011 EVALUATION OF WATER RECLAMATION AND REUSE This Plan evaluates the potential for wastewater reuse from the WWTP. Wastewater reuse can potentially be cost-effective by generating revenue from selling reclaimed effluent to customers for non-potable uses, while providing environmental benefits. This section presents a brief evaluation of the feasibility of reusing effluent from the WWTP. Chapter 4, in part, covers regulations concerning water reuse. The Washington State Water Reclamation and Reuse Standards define four classes of reclaimed water (Classes A, B, C and D), distinguished by treatment technologies and the final bacterial concentration. Class A reclaimed water, the highest classification, is generally required for uses with potential for public contact, such as would be encountered in the City. Under RCW 90.46, Class A reclaimed water means reclaimed water that, at a minimum, is at all times an oxidized, coagulated, filtered, disinfected wastewater. To meet Class A reclaimed water standards, the facility effluent must be coagulated and filtered in order to meet a turbidity standard. Reclaimed water must be disinfected to meet a coliform standard that is much stricter than the standard for secondary effluent. In addition, reclaimed water processes must meet the reliability and redundancy requirements in the state standards. Generally, the state standards require system storage capacity, for interruptions in the final reuse system, and bypass storage, to store partially treated wastewater that does not meet the reclaimed water standards. Where no alternative reuse or disposal system exists, system storage capacity shall be the volume equal to three times that portion of the daily flow of reuse capacity, and bypass storage at least one times that volume. However, the City is permitted for discharge to Puget Sound based on limits established for CBOD5, TSS, ammonia, and fecal coliform. It is possible that the City can meet its NPDES discharge limits, yet at times not meet all of the limits for Class A reclaimed water. Thus, storage at the WWTP may not be a requirement. The City can utilize its outfall or the Everett discharge in these instances. Potential for Reuse Potential uses of reclaimed water for the City are limited, but several possible beneficial uses are discussed below. Most of these potential uses would require Class A reclaimed water. Industrial Cooling Water One potential use for reclaimed water is industrial cooling water for cogeneration power plants. The city has been approached over the past several years by more than one company that was interested in using the city’s effluent for this purpose. However, no interest has been shown recently for this use. 8-8 City of Marysville November 2011 Sewer Comprehensive Plan Irrigation/Landscaping Use Potential uses of reclaimed water include irrigation of park grounds and golf courses. In the vicinity of the WWTP is Jennings Nature Park (31 acres) and Jennings Memorial Park (20 acres). The Jennings Memorial Park is primarily used for recreational facilities, including baseball and play areas. About 2 miles northeast of the WWTP is the 120-acre Cedarcrest Golf Course. The golf course is owned and operated by the City of Marysville Parks and Recreation Department. Fire Protection Reclaimed water can be used for fire protection in hydrants and sprinkler systems located in commercial or industrial facilities, hotels, and motels. Ground Water Recharge Another possible use for reclaimed water is ground water recharge or aquifer replenishment. Other Possiblities Possible uses for reclaimed water by the City’s public works department includes using the water in street sweepers, to wash down streets, to flush sanitary sewer lines, or as washdown water at its wastewater treatment plant. Offsets to Existing Water Rights The service area for the City of Marysville is supplied potable water from several different sources as presented in Table 8-3. City of Marysville 8-9 Sewer Comprehensive Plan November 2011 TABLE 8-3 Sources of Supply for the Marysville Coordinated Service Area(1) Primary Supply Source Reliable Capacity (mgd) Water Rights (mgd) Everett-Marysville Pipeline 13.15 13.15 Stillaguamish Ranney Collector 3.2 3.2 Edward Springs 2.5 2.1 Lake Goodwin Well 0.5 0.8 Subtotal 19.35 19.25 Secondary Supply Source Highway 9 Well 1.4 1.4 Sunnyside Well No. 2 1.1 1.1 Subtotal 2.5 2.5 Total 21.85 mgd 21.75 mgd (1) City of Marysville 2009 Water System Plan Update. Based on the City’s Water System Plan, the projected demands for 2028 are 16.6 mgd average day, and 22.9 mgd peak day. In addition, the City of Everett has certified water rights of 246 mgd for its overall service. Currently, the City of Everett operates its filtration plant at less than 100 mgd. Because of existing and potential water rights, use of reclaimed water would have a minimum impact offsetting water rights. Wetlands Flow Augmentation Reclaimed water can be used to augment flow in wetland areas. In fact, the City has created a wetland area near its WWTP which is now classified as a natural wetland area. However, other wetland areas are owned by the Tulalip Tribes. The Tribe has not expressed any interest for use of its wetland areas for this purpose. Of the potential uses for reclaimed water, irrigation/landscaping provides the highest and most reasonable alternative for reuse. This alternative is presented in more detail below. CONCEPTUAL DESIGN AND COST ESTIMATE Irrigation Demands Irrigation rates were estimated from the net irrigation demands listed in the Washington State Irrigation Guide for turf grass at the Everett Station. The annual net irrigation demand is 13 inches/year with an irrigation season from mid May to mid November (6 months/year). The irrigation demand varies during the irrigation season, with the peak irrigation demand in July (4.46 inches). Table 8-4 lists estimated potential reclaimed water usage for irrigation. 8-10 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 8-4 Potential Irrigation Use for Reclaimed Water Irrigation Area Irrigated Area (acres) Annual(1) Usage (MG/year) Peak(2) Day (gpd) Cedar Crest Golf Course 120 42.40 605,000 Jennings Memorial Park(3) 10 3.6 50,000 Jennings Nature Park(4) 10 3.6 50,000 Total 140 49.6 705,000 (1) Annual irrigation usage based on 13 inches per year over a 6-month irrigation season per Washington State Irrigation Guidelines, Everett location. (2) Peak day irrigation usage based on an irrigation demand of 4.46 inches in July. (3) Estimated irrigated area 50 percent of total. (4) Estimated irrigated area 33 percent of total. According to the Water Reclamation and Reuse Standards, Class A reclaimed water is required for irrigation of public areas. The estimated peak day demand is 705,000 gpd, approximately 15 percent of the current annual average flow. Production of Reclaimed Water The WWTP currently produces secondary effluent for discharge to Puget Sound. Production of Class A reclaimed water would be required for irrigation of public contact areas. As production of reclaimed water is more expensive then secondary effluent, it is recommended to develop a sidestream water reclamation process. Several alternatives are available for production of reclaimed water. Under RCW 90.48, Class A reclaimed water must be continuously oxidized, coagulated, filtered and disinfected. The existing facility provides the oxidation step so the sidestream process must contain a coagulation system, filter, and UV disinfection system. The Class A reclamation sidestream would be operated when there is a demand for irrigation water. At other times, and in case Class A reclamation standards are not met, the sidestream would shutdown and the main facility would process and discharge (alternate disposal system). Reclaimed water system storage or bypass storage is not required. The reclaimed water sidestream will be sized to provide the annual average demand with a 25 percent factor for additional capacity. Peak day demand will be met with off-site storage. The average annual usage is 49.6 MG, but distributed over a 180-day period. The design capacity is 0.275 mgd plus 25 percent, or 0.34 mgd. Rounding up, the design of the sidestream reclaimed water system would be 0.35 mgd. Coagulation and Filtration Existing coagulation chemical feed equipment and sand filters are used at the WWTP. The filtration system is a continuous, monomedia type which will tripled to 2,400 square feet of filter surface area in the 2004 Phase 2 plant upgrade. The coagulation chemical City of Marysville 8-11 Sewer Comprehensive Plan November 2011 feed system uses alum at a dosage of 100 mg/L. There are three metering pumps and three alum storage tanks. Recent performance data show that the filters produce an effluent with an average TSS of 22 mg/L. Therefore, it is not expected that the filters are capable with the current feed and loading to produce an effluent turbidity less than 2.0 NTU as required for reuse standards. Therefore, a separate sidestream filter process should be constructed. To meet Class A reclaimed water standards, the coagulation and filtration equipment would need to be continuously monitored to ensure filtered turbidity of less than 2.0 NTU. UV Disinfection System The WWTP has a UV system but it is designed for secondary effluent standards. For Class A reclaimed water, the UV disinfection system must be capable of disinfecting filtered secondary effluent to produce an effluent with 2.2 total coliform/100 mL (weekly median). The effluent UV transmittance (a measure of UV absorbance by dissolved or suspended materials in the water) was estimated at 60 percent, for filtered Marysville effluent based on field measurements. The National Water Research Institute has developed guidelines for UV disinfection, which recommend a design dose of 100 mJ/cm2 for production of reclaimed water from media-filtered effluent. The reclaimed water UV disinfection system will be a low pressure, horizontal, high intensity UV system consisting of three reactors in series, one as standby. Each UV lamp is capable of disinfecting 5 gpm per lamp. Based on this criteria, 75 lamps will be provided, 25 lamps per reactor. Alarms and Telemetry The use of reclaimed water for irrigation in open access areas demands a higher level of quality control than normal WWTP operations. An alarm system will be installed to notify staff if the coagulation, filtration, or disinfection systems fail, or if the reclaimed water quality falls below an acceptable level. The level of the reclaimed water reservoir described production control system. At this point, the reclaimed water production will cease and effluent will be recycled back to the lagoon system. Distribution and Storage The layout of the distribution system is shown in Figure 8-2. Irrigation of public access areas, such as schools, must be performed at the time when risk of public contract is least (nighttime). Assuming a 6-hour irrigation period (11:00 p.m. to 5:00 a.m.), the peak day irrigation demand is 1,960 gpm (705,000 gpd/6 hr). Instead of producing reclaimed water at this rate, it is more cost effective to operate the reclaimed water facility 24 hours per day at a lower rate, and 8-12 City of Marysville November 2011 Sewer Comprehensive Plan provide irrigation distribution storage. Approximately 600,000 gallons of storage will be required for equalization located in the vicinity of the Cedarcrest Golf Course. A pump station and transmission main will convey the reclaimed water from the WWTP to the irrigation storage reservoir. The elevation at the discharge of the reclamation facility would be about 5 feet and the elevation at the irrigation area is about 105 feet. The pumps (one duty, one standby) will be rated at 500 gpm at 140 total dynamic head (TDH). The motor horsepower will be 40 hp, 3 phase. Total irrigation supply pumps will be provided to transfer reclaimed water from the storage reservoir to the golf course irrigation system. Three of the pumps will operate to provide the necessary irrigation demand in 6 hours. One pump will be standby. Each pump will be sized for 560 gpm at 70 psi to produce sufficient pressure for golf course irrigation. The motor horsepower will be 50 hp each. Irrigation for the smaller areas in Jennings Park will be provided from the transmission main and pump station. Approximately 17,900 LF of 8-inch pipe will be required between the WWTP and the storage reservoir located on the golf course, primarily following City rights-of-way. An additional 1,500 LF of pipe has been estimated to supply reclaimed water from existing irrigation connections. ECONOMIC FEASIBILITY OF REUSE Production of reclaimed water is economically feasible if the cost of producing and distributing reclaimed water is less than the cost of purchasing potable water. The economic feasibility of reuse if evaluated by comparing the annualized cost of providing reclaimed water ($/gal.) with the current purchased price. The City’s water billing is based on a meter size and then a volume change over a certain use. For the two smaller connections at Jennings Park, a 4-inch meter is assumed. For a 4-inch meter, the bimonthly meter charge is $310 with an allowance of 150,000 gpd. For use in excess of 150,000 gallons, the volume charge is $2.02/1,000 gallons. Similarly, for a 6-inch meter, the meter charge is $735 with an allowance of 150,000 gallons. For the annual usage estimate in Table 8-5; the estimated cost for potable water is $101,530. Capital costs for constructing the treatment, storage and distribution system are summarized in Table 8-5. City of Marysville 8-13 Sewer Comprehensive Plan November 2011 TABLE 8-5 Capital Cost Estimate for Water Reuse System Item Quantity Unit Unit Price Total Price Mobilization/Demobilization 1 LS $150,000 $ 150,000 Class A Filtration System 1 LS $200,000 $ 200,000 Class A UV Disinfection System 1 LS $245,000 $ 245,000 Alarms and Instrumentation 1 LS $ 25,000 $ 25,000 Reclaimed Water Pump Station 1 LS $150,000 $ 150,000 Reclaimed Water Pipeline 17,900 LF $ 75 $1,327,500 Reclaimed Water Reservoir 1 LS $600,000 $ 600,000 Irrigation Supply Pumping Station 1 LS $160,000 $ 160,000 Irrigation Supply Piping 1,500 LF $ 60 $ 90,000 Subtotal $2,941,500 Contingency (20%) $ 589,500 Subtotal $3,537,000 Sales Tax $ 314,793 Total Construction Cost $3,851,793 Engineering and Administrative Costs (25%) $ 962,948 Total Estimated Project Cost (Rounded) $4,800,000 The estimated annual operation and maintenance cost for the reclaimed water system is per year, as shown on Table 8-6. TABLE 8-6 Annual O&M Cost Estimate for Water Reuse System Item Annual Quantity Unit Unit Price Annual Cost Labor (2 hr/day) 240 HR $35 $8,400 Electricity 180,000 kWhr $0.07 $12,600 Maintenance(1) 1 LS $17,400 Lab/Miscellaneous 1 LS $10,000 Total Annual Cost $48,400 (1) 3 percent of capital cost of new equipment. Table 8-7 provides a comparison of the annual cost for reclaimed water to the existing cost for irrigation with potable water. The annualized debt service based on a 20-year 1.5 percent PWTF loan for the capital cost would be $279,360/year. Combined with the additional O&M cost of $48,000, and the annual average demand of 49.6 MG, the cost for reclaimed water would be $6.60 per 1,000 gallons. 8-14 City of Marysville November 2011 Sewer Comprehensive Plan The annual cost for potable water is $101,530 or equivalent to $2.05 per 1,000 gallons. Therefore, production of reclaimed water does not appear to be economically feasible at this time. TABLE 8-7 Comparison of Reclaimed Water and Potable Water Costs Water Reuse Alternative Potable Water Use Capital Cost $4,800,000 N/A Annual O&M Cost $ 48,400 $101,530 20-Year Present Worth(1) $5,630,960 $1,743,067 Annual Debt Payment $ 279,360 N/A Total Annualized Cost $ 327,760 $101,530 Cost of Water ($/1,000 gal) $6.60 $2.05 (1) 1-1/2 percent, 20-year basis for present worth. WWTP CLASS "A" WATER RECLAMATION SIDE STREAM FACILITY AND PUMP STATION JENNINGS PARK RECLAIMED WATER8" PIPELINE CEDARCRESTGOLF COURSEIRRIGATIONRESERVOIR SR 9SR 529GROVE ST 83RD AVE NE27TH AVE NE64TH ST NE 108TH ST NE 4TH ST 88TH ST NE CEDAR AVE8TH STBEACH AVE44TH ST NE 71ST AVE NE79TH AVE NESUNNYSIDE BLVD80TH ST NE 48TH DR NE61ST ST NE 40TH ST NESHOULTES RD76TH ST NE M A R IN E D R N E I-588TH ST NE 51ST AVE NE100TH ST NE 51ST AVE NE84TH ST NE SUNNYSIDE BLVDSewer Comprehensive Plan Proposed Reclaimed Water System Figure 8-2 0 2,000 4,000 6,0001,000 Feet Proposed reservoir Proposed pipeline Sewer trunk lines Sewer Lines Sewer service area (UGA) City of Marysville 8-15 Sewer Comprehensive Plan November 2011 WWTP RECOMMENDED IMPROVEMENTS This plan includes several recommended mechanical improvements for the current plan period as shown below. • Replacement or reconstruction of the concrete influent parshall flume at the headworks of the plant, or to install a fiberglass insert to correct the current deficiencies in the flow measurement there. The existing concrete structure would need to be resurfaced and leveled. This work is projected to be completed in year 2013 and the budgetary cost is projected at $50,000. • Extension of the filter reject line from the West Trunk Pump Station to Complete Mix Cell 1A at the headworks of the plant. This work is projected to be completed in the year 2013 and the budgetary cost is projected at $117,000. • Upsizing of the filter reject pump station wet well and pumps. This work is projected to be completed in year 2014 and the budgetary cost is projected at $500,000. • Construction of a pre-settling basin to allow flocculation and settling prior to effluent filtration. This work is projected to be completed in year 2015 and the budgetary cost is projected at $1,000,000. • Replace the existing barscreens with a barscreen that has a 3/8” or smaller bar spacing, or replace with an alternative screen that meets the 3/8” spacing requirement. This work is projected to be completed in year 2017 and the budgetary cost is projected at $500,000. • A preliminary biosolids profile is scheduled for year 2016. This will be used to assess the need for biosolids removal, but it is not anticipated that the removal will take place within this 6 year comprehensive plan. Future planned WWTP improvements, outside of the current plan period, include the addition of aerated cells #7 and #8, and addition of alum storage capacity. (Capital Facilities Plan, KCM 2001). These improvements will be assessed as future flows and loadings increase. Table 8-8 provides a list of both capital improvements and other recommendations for the WWTP. 8-16 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 8-8 Recommended WWTP Improvements and Actions Description Year Replacement or reconstruction of the Headworks Parshall Flume 2013 Extension of the Filter Reject Line to Complete Mix Cell 1A 2013 Upsizing of the Filter Reject Wet Well and Pumping System 2014 Pre-Settling Basin prior to Effluent Filtration 2015 Preliminary Biosolids Profile 2016 Screen Replacement for the Mechanical Barscreens 2017 Costs associated with these improvements are also summarized in Chapter 11, Capital Improvement Plan. City of Marysville 9-1 Sewer Comprehensive Plan November 2011 CHAPTER 9 BIOSOLIDS MANAGEMENT GENERAL This Chapter discusses and estimates the quantity and quality of biosolids that accumulate in the oxidation ponds of the City’s WWTP. Information on biosolids is based on data found in the 1997 Comprehensive Sanitary Sewer Plan, testing data from 2002 provided by Hammond Collier & Wade-Livingstone Engineers, and other information provided by City staff. The City removed approximately 4,300 dry tons of biosolids from its oxidation ponds in 2003. This quantity represented an accumulation of 40 years, primarily in the south end of the ponds. The method used was dredge and dewater, hauling, and land application. The cost was about $1.4 million exclusive of trucking costs. This Chapter also presents a discussion of biosolids regulations and future management of biosolids. BIOSOLIDS REGULATIONS Regulations pertaining to biosolids include 40 CFR Part 503, WAC 173-308, and WAC 173-200. 40 CFR PART 503 40 CFR Part 503, regulating the disposition of municipal sewage sludge, went into effect in 1993. The 503 rule applies to the sewage sludge generated from municipal wastewater systems, i.e., municipal wastewater treatment systems, and domestic septic tanks. EPA allows states the ability to enforce their own version of biosolids regulations. Under 40 CFR 503, these state biosolids regulations must be at least as stringent as the federal 503 regulations. WAC-173-308 BIOSOLIDS MANAGEMENT The State of Washington has adopted the 503 requirements in its own regulations governing the use or disposal of biosolids, WAC 173-308. These regulations became effective in March 1998 and are enforced by the State Department of Ecology (Ecology). The requirements in WAC 173-308 are very similar to the requirements of the federal 503 regulations. 9-2 City of Marysville November 2011 Sewer Comprehensive Plan There are three fundamental elements of the federal 503 and state 308 regulations that establish minimum criteria for beneficial use of biosolids: (1) pollutant concentrations and application rates (2) pathogen reduction measures (3) vector attraction reduction measures Trace Pollutant Concentrations and Application Rates Maximum allowable concentrations in biosolids are established for nine heavy metals (arsenic, cadmium, copper, lead, mercury, molybdenum, nickel, selenium and zinc). If a biosolids sample exceeds the ceiling concentration of any of these metals, it cannot be land applied. A second pollutant threshold concentration is identified for Exceptional Quality (EQ) biosolids. If biosolids are shown to be below these concentrations, they may be considered EQ, and thus be eligible for relatively unrestricted land application, provided they meet other EQ requirements. To be considered “EQ,” biosolids must not only meet the EQ pollutant requirement, but also meet Class “A” pathogen reduction requirements and vector attraction reduction requirements (see below). Cumulative trace pollutant loading rates for biosolids are designated for these nine heavy metals. These rates cannot be exceeded during the life of an application site. Once a cumulative loading limit is reached for a particular limiting pollutant, the land can no longer receive biosolids containing any level of the limiting pollutant. Annual trace pollutant loading rates are also set for the same nine heavy metals. Pathogen Reduction Requirements In order for biosolids to be land applied, they must meet specific criteria demonstrating a minimum level of treatment to reduce the density or limit growth of pathogenic bacteria. By meeting these minimum criteria, a biosolids sample is referred to as meeting Class “B” pathogen reduction requirements. The term "Class B biosolids" is sometimes erroneously referred to as any biosolids meeting all minimum criteria that allow the biosolids to be land applied, which is not the case. Biosolids must meet vector attraction reduction requirements and minimum pollutant concentration standards as well as Class “B” pathogen reduction requirements (at a minimum) in order to be acceptable for land application. Class “B” biosolids must meet one or more of three alternative criteria for pathogen reduction described in the 503 and 308 regulations. The 503 and 308 regulations provide six alternative methods to demonstrate that biosolids are Class “A” with respect to pathogens. When biosolids meet the Class “A” standard, they are subject to fewer restrictions for land application as long as they also meet the lower (WAC-173-308) Table 3 pollutant concentration thresholds and vector attraction reduction standards. City of Marysville 9-3 Sewer Comprehensive Plan November 2011 Vector Attraction Reduction Requirements The third minimum requirement for biosolids to be land applied is the vector attraction requirement. This measure is designed to make the biosolids less attractive to disease- carrying pests such as rodents and insects. These measures typically reduce the liquid content and/or volatile solids content of the biosolids or they make the biosolids relatively inaccessible to vector contact by soil injection or tilling. The 503 and 308 regulations list seven alternative treatment techniques and/or laboratory tests that would qualify a sludge as meeting vector attraction reduction requirements. If biosolids are not treated by one of the listed treatment techniques to provide vector attraction reduction, and if it does not pass the laboratory tests for vector attraction reduction, then it can meet the requirements during land application by subsurface injection or immediate tilling into the ground. Management Practices For biosolids that are Class “B” with respect to pathogens and have met the three criteria discussed above, the 503 and 308 regulations identify specific management practices that must be followed during land application of biosolids. The biosolids must be applied at a rate that is equal to or less than the agronomic rate. The placement of biosolids on land cannot adversely affect a threatened or endangered species. Biosolids cannot be applied to ground in a manner that would cause it to enter wetlands or a surface water body (e.g. on frozen ground or snow-covered ground) nor can it be applied within 10 meters or less of surface water. Class “B” biosolids may not be applied to lawns or gardens. If biosolids meet lower pollutant threshold limits, Class “A” pathogen reduction requirements, and vector attraction reduction requirements, they are eligible for relatively unrestricted application. Biosolids in this category are referred to as "Exceptional Quality" (EQ). EQ biosolids can be containerized and sold or given away in quantities up to one metric ton provided a label or information sheet is provided with: (1) the biosolids preparer's name and address, (2) sufficient information (nitrogen concentrations) for the recipient to determine an agronomic rate of application, (3) a statement that application is prohibited except in accordance with instructions provided with the container. Monitoring Requirements Monitoring frequencies are based on quantities of biosolids produced. (It is not generally necessary to verify that pathogen and vector attraction reduction measures are met for 9-4 City of Marysville November 2011 Sewer Comprehensive Plan each individual load of biosolids that is land applied, per WAC 173-308-150 (3)). The actual monitoring frequencies will depend on the frequency of applications. Record-keeping, Reporting and Certifications The 503 and 308 regulations have specific record-keeping, reporting, and certification requirements for land application of biosolids. The general biosolids permit implements requirements for record keeping and reporting in accordance with WAC 173-308-290 and –295. Records must be kept for meeting all pathogen reduction and vector attraction reduction requirements for biosolids and domestic septage. For biosolids, records must be kept of analyses performed for meeting trace pollutant criteria. Ecology requires that all facilities, regardless of size, make annual reports to both Ecology’s headquarters and the appropriate regional office, by March 1st of each year. Permitting WAC-173-308-310 lists permitting requirements for municipalities managing biosolids. The primary permit required for biosolids management activities is the State General Permit for Biosolids Management. The permittee must carry out public notice as required under WAC 173-308-310(11), and public hearings if required, in accordance with WAC 173-308-310(12), and comply with requirements of the State Environmental Policy Act (SEPA) as stipulated under WAC 173-308-310(030). Treatment works treating domestic sewage that come under the State general permit must also comply with requirements of the State Environmental Policy Act (SEPA) per WAC 173-308-030. The Department of Ecology carries out public notice as a part of the process of issuing a general permit. Public notice requirements for facilities subject to this permit vary depending on the purpose the notice is serving and the quality of biosolids being managed. When a facility applies for initial coverage under the general permit it must carry out public notice for that purpose as specified in WAC 173-308- 310(11). Notification must be made to the general public, affected local health departments, and interested parties. WAC-173-308-205 SIGNIFICANTLY REMOVE MANUFACTURED INERTS WAC-173-308-205 requires all biosolids (including septage) or sewer sludge to be treated by a process such as a physical screening or another method to significantly remove manufactured inerts prior to final disposition. Meeting this requirement may occur at any point in the wastewater treatment or biosolids manufacturing process. Meeting the requirements can be accomplished by either of the following methods: (a) Screening through a bar screen with a maximum aperture of 3/8 inch (0.95 cm). City of Marysville 9-5 Sewer Comprehensive Plan November 2011 (b) Obtaining approval from the Department of Ecology for an alternative method that achieves a removal rate similar to or greater than that achieved by the screening standard in (a). The requirements of WAC-173-308-205 must be met by July 1, 2012, or at the time of final disposition if the material will not be managed prior to July 1, 2012. The City looked into retrofitting their existing John Meunier bar screens to meet the new requirement, and found that they could only be reduced to a minimum 1/2 inch spacing which did not meet the department’s requirement. After looking at several alternative bar screen makers and alternative screening options and the capital cost for each, the City has opted to have the biosolids screened at the time of removal from the lagoons by the contractor. This method for meeting the requirement was discussed with the Department of Ecology and was addressed in the City’s 2010 Application for Coverage Under the General Permit for Biosolids Management. BIOSOLIDS QUALITY AND CHARACTERISTICS Table 9-1 presents the metals concentrations and other characteristics for biosolids from the City’s oxidation ponds in 1994. Results from a 1994 hydrographic survey and sampling program (Hammond Collier & Wade-Livingstone, 1994) showed that biosolids accumulated in two zones. The “high solids zone” was located at the south end of the ponds. The “low solids zone” was the remaining areas in the ponds. Biosolids characteristics for both areas are presented in Table 9-1. In 2003, Hammond Collier & Wade-Livingstone conducted additional sampling for the City’s oxidation ponds prior to the biosolids removal project in 2003. These results are presented in Table 9-2 for metal concentrations and other biosolids characteristics. In addition to metals and solids characteristics, the City’s biosolids were also analyzed for PCBs, pathogens, and vector attraction requirements. PCBs were found to be 1.0 mg/kg, or less. Pathogen testing showed the density of fecal coliform to be significantly less than the standard of 2,000,000 Colony Forming Units (FCUs) per gram of total solids (dry weight basis). In addition, vector attraction requirements were met in all cases. 9-6 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 9-1 Pollutant and Other Characteristics in Biosolids from Marysville WWTP (1994 Sampling Data) Parameter Metals Units Low Solids Zone High Solids Zone WAC-173-308 Table 3 Threshold (EQ) Compliance (Y/N) WAC-173-308 Table 1 Ceiling Conc. Limits Compliance (Y/N) Arsenic mg/kg 32 24 41 Yes 75 Yes Cadmium mg/kg 8 5.6 39 Yes 85 Yes Copper mg/kg 305 277 1,500 Yes 43 Yes Lead mg/kg 168 197 300 Yes 810 Yes Mercury mg/kg 6 1.3 17 Yes 57 Yes Molybdenum mg/kg 75 Nickel mg/kg 66 63 420 Yes 420 Yes Selenium mg/kg 32 22 100 Yes 100 Yes Zinc mg/kg 560 637 2,800 Yes 7,500 Yes Other Characteristics(1) Total Acre of Oxidation Ponds acres 44 23 67 N/A N/A N/A Volume cubic yard 76,985 34,100 111,085 N/A N/A N/A Solids Content percent 3.35 6.3 N/A N/A N/A N/A Mass Dry Solids tons 2,170 2,150 4,320 N/A N/A N/A Percent of Total percent 50% 50% 100% N/A N/A N/A (1) Results of the Lagoon Hydrographic Survey Results, Hammond, Collier & Wade-Livingstone, 1994. City of Marysville 9-7 Sewer Comprehensive Plan November 2011 TABLE 9-2 Pollutant and Other Characteristics in Biosolids from Marysville WWTP (2002Sampling Data)(1) Parameter Metals Units Low Solids Zone (N) High Solids Zone (S) WAC-173-308 Table 3 Threshold (EQ) Compliance (Y/N) WAC-173-308 Table 1 Ceiling Conc. Limits Compliance (Y/N) Arsenic mg/kg 28 26 41 Yes 75 Yes Cadmium mg/kg 4.9 5 39 Yes 85 Yes Chromium mg/kg 359 357 N/A N/A N/A N/A Copper mg/kg 287 338 1,500 Yes 43 Yes Lead mg/kg 147 143 300 Yes 810 Yes Mercury mg/kg 1.63 2.97 17 Yes 57 Yes Molybdenum mg/kg 9.38 7.95 N/A N/A 75 N/A Nickel mg/kg 77 67 420 Yes 420 Yes Selenium mg/kg 6.9 7.8 100 Yes 100 Yes Silver mg/kg 18.3 21.4 N/A N/A N/A N/A Zinc mg/kg 635 803 2,800 Yes 7,500 Yes Other Characteristics Ammonia mg-N/kg 1,508 1,983 N/A N/A N/A N/A N-NO3 NO2 mg-N/kg 3.0 3.7 N/A N/A N/A N/A O-Phos mg-P/kg 63 175 N/A N/A N/A N/A PCB mg/kg <1 <1 N/A N/A N/A N/A Sulfate mg/kg 2,220 2,850 N/A N/A N/A N/A T-Phos mg/kg 4360 7,967 N/A N/A N/A N/A TKN mg/N/kg 21,000 23,650 N/A N/A N/A N/A Solids Content percent 10.3 15.3 N/A N/A N/A N/A (1) Results for the Biosolids Removal Project, Hammond, Collier & Wade-Livingstone, 2002. 9-8 City of Marysville November 2011 Sewer Comprehensive Plan In both Tables 9-1 and 9-2, the analytical results for metals are compared with the pollutant limits listed in WAC 173-308. Generally, the higher the concentration of pollutants the more restricted disposal options will be. If any of the WAC 173-308 Table 1 ceiling concentration limits are exceeded, the sludge is considered a solid waste, not biosolids, and cannot be beneficially reused. If all of the pollutant concentrations are below the Table 3 limits from WAC 173-308, the sludge is eligible for “EQ-exceptional quality” status and thus relatively unrestricted management alternatives (assuming appropriate pathogen reduction and vactor attraction measures are employed). The City’s biosolids, as shown in Table 9-1 and Table 9-2, satisfied the requirement for metals concentration for EQ biosolids. Another requirement for land application is pathogen removal. To be classified as Class “B,” fecal coliform concentration must be less than 2,000,000 MPN/gram. To meet Class “A” standards, the fecal coliform concentration must be less than 1,000 MPN/gram. Analyses conducted in 2002 indicate that the City’s biosolids complies with this requirement for Class “A.” In order to land apply the biosolids as Class “B,” with respect to the pathogen removal, the City must perform the following tests during the process of applying for the Biosolids General Permit: • Fecal coliform concentration (seven samples) • Pollutant concentrations, including metals and PCBs. • Vector attraction reduction, particularly the long-term anaerobic degradability bench test. In order to land apply biosolids as Class “A,” EQ biosolids, the City must perform the following tests in addition to those for Class “B”: • Enteric virus concentrated • Viable helminthova concentrations The 1994 analytical results showed an average concentration of total solids of 4.8 percent. The 2002 date showed a range for the north and south lagoon areas of 10 to 15 percent. Typical values for lagoon sludge are 3 to 15 percent, therefore, the City’s concentration is considered normal. The change in solids content from 4.8 percent in 1994 to an average of 12.8 percent in 2002 can be partly explained by the additional settling time. The additional time allows additional consolidation of biosolids within the oxidation ponds. However, predicting the change in solids content is difficult. In this case, the change was 8 percent in only 8 years. City of Marysville 9-9 Sewer Comprehensive Plan November 2011 BIOSOLIDS MANAGEMENT In the 2001 Capital Facilities Plan (TetraTech/KCM, Inc.), three biosolids management alternatives were evaluated: • Low rate lagoons • High rate lagoons • Mechanical solids handling The recommended alternative was the low rate lagoons, the system which has been in place for the past 40 years. The Capital Facilities Plan stated that if the selected liquid-stream process was an activated sludge process, then the mechanical solids handling would be required. However, because Phase 2 construction was an expanded aerated lagoon system, biosolids storage, or the low rate lagoons, will continue as part of the City’s plan. The complete components of this low-rate lagoon plan included continued storage of biosolids in the oxidation ponds and periodic removal by contract dredging, dewatering, and disposal of the accumulated biosolids at an approved beneficial use facility. A contractor will dredge the oxidation ponds, then dewater the biosolids onsite (approximately 20 to 25 percent solids) with a mobile dewatering system. Biosolids that meet the criteria for disposal at a contracted land application facility are transported by the contractor and disposed at such a facility. Beneficial use facilities are located in Cinebar, Lewis County (Fire Mountain Farms), Mansfield, Washington (Boulder Park), and other eastern Washington sites. As presented in Table 9-1, the City’s biosolids do meet some of the criteria for Class “A” EQ biosolids. However, the complete analysis conducted in 2002 resulted in a Class “B” biosolids classification. For future biosolids removal projects where Class “B” biosolids are land applied at a beneficial use facility, the City must complete the following: • Application for coverage under the Statewide General Permit for biosolids. This action will include SEPA and public notice for the hauling activity in Snohomish County and in the County where biosolids will be land applied. The beneficial use facility will already have been permitted for its site. • Signed certification statements that the biosolids meet all application quality regulations. • Annual report to Ecology including laboratory results and records of amount of biosolids that were land applied. 9-10 City of Marysville November 2011 Sewer Comprehensive Plan • Measure and report the nitrogen concentration in the biosolids to the operators of the beneficial use facility. • A contract with a Contractor(s) to dredge, dewater, haul and land apply the Class “B” biosolids. A contractor would use an auger-head dredge unit to remove the accumulated biosolids from the oxidation ponds. Portable polymer feed and dewatering equipment, such as a centrifuge or a belt filter press, would be installed on site to dewater the biosolids to 20 to 25 percent. The dewatered biosolids would be deposited into a truck for transport to the beneficial use facility for land application. The impact on current City staff would be temporary since the dredging, dewatering and hauling operation can be completed in 4 to 6 months. For contract hauling and land application of Class “B” biosolids, the primary challenge for the City staff is to plan for the next biosolids removal project since biosolids were last removed from the oxidation ponds in 2003. The schedule for the next removal project is dependent upon a variety of factors, which are listed below: • Loading rates to the WWTP • Solids content of accumulated biosolids • Percentage of oxidation ponds volume with accumulated biosolids • Inert solids concentration Most of these factors are considered in the following equation which calculates annual sludge accumulate rate: Ry = 365 QXi x Where: RY = annual accumulation rate, m3/yr Q = average wastewater flow rate, m3/day Xi = inert solids, mg/L x = weight fraction of solids in the sludge, and = density of water = 106g/m3 (Equation 4.4.1-High Performance Aerated Lagoon Systems, Linvil Rich, 1999.) This equation can be modified slightly so that the annual accumulation rate is presented in cubic yards per year. This unit is consistent with previous work which characterizes the oxidation pond volume in terms of cubic yards. The modified equation with the appropriate conversion units is shown below: City of Marysville 9-11 Sewer Comprehensive Plan November 2011 Ry = 365 QXi x (7.48 gal/ft3) (27 ft3/yd3) Where: RY = annual accumulation rate, yd3/yr Q = average wastewater flow rate, mgd Xi = inert solids, mg/L x = weight fraction of solids in the sludge, and = density of water = 1 g/mL Based on work completed for this Plan and references from previous work, information about several of these factors is available. Existing and projected flows are shown in Table 6-10. The weight fraction of solids in the sludge is an average of 4.8 percent (Wastewater Treatment Hydrographic Survey and Biosolids Evaluation for the High Solids Zone, HCW-L, 1996.) For this evaluation, the solids content value is rounded up to 5 percent. The primary unknown is the inert solids concentration. The City’s WWTP does not have grit removal facilities at the headworks therefore a primary component of the accumulated biosolids would be expected to consist of inert material. One reference for this inert solids value is High Performance Aerated Lagoon Systems (Rich, 1999). In the discussion for inert solids concentration, Rich notes that solids that are subjected to stabilization processes over a period of several years can be expected to display higher biodegradability than shorter processes such as 1 month. Furthermore, he states that solids at 4 percent in a stabilized sludge that have been observed to accumulate over a period of years, in aerated lagoon sludges, lead to an estimate of Xi of about 90 mg/L. Comparing this inert concentration of 90 mg/L with the influent TSS concentration of 254 mg/L (Table 6-2) results in an inert fraction of 35 percent. According to Metcalf & Eddy, a high strength wastewater, such as the City’s, could be expected to contain 75 mg/L as “fixed” or inert solids. However, other solids formed by the biological process in the aerated lagoon will settle in the oxidation pond and stabilize over a period of years. Most of these solids, but not all, will be converted to methane, ammonia, and other reduced compounds. A small fraction will accumulate as inert material. Based on the high concentration of influent TSS and the processes in the oxidation ponds, a value of 90 mg/L would appear to be representative of the inert solids in the oxidation ponds. With this value of 90 mg/L for Xi, the annual accumulation of biosolids can be estimated from the equation presented above. For the existing WWTP flow of 4.5 mgd, the annual biosolids accumulation is 14,635 yd3/year with a 5 percent solids content as shown below: 9-12 City of Marysville November 2011 Sewer Comprehensive Plan Ry = 365 (4.5 mgd) (90 mg/L) (0.05) (1 mg/mL)(7.48 gal/ft3) (27 ft3/yd3) = 14,635 yd3/year Typically, biosolids are removed from wastewater lagoons every 10 to 20 years. A better approach, however, is to establish a volume accumulation which would then establish the next removal schedule. The 1996 HCW-L Report suggested 20 percent of the lagoon volume as the basis for the need for the biosolids removal operation. The percentage volume amounts to about 130,000 cubic yards. The solids content of the biosolids within the oxidation ponds is a significant variable determining when the 20 percent level will be reached. In addition, based on the available data, it is a variable which will change over time. The 1994 data showed an average solids content of 4.8 percent but by 2002 it had increased to 12.8 percent. The higher solids content means that less of the pond is utilized for biosolids accumulation and that the schedule for the next biosolids removal project can be extended. Table 9-3 illustrates the potential difference with an average solids content of 5 percent and 10 percent. The 5 percent solids represents the results of the 1994 sampling and 10 percent the average for the north lagoon in 2002. It is not known what solids content will be representative when 20 percent biosolids accumulation is reached in the future. TABLE 9-3 Biosolids Accumulation Rates Year Average Annual Flow (mgd)(1) 5 Percent 10 Percent Annual Biosolids Accumulation (yd3/year)(1) Cumulative Total in Lagoons (yd3) Annual Biosolids Accumulation (yd3/year)(2) Cumulative Total in Lagoons (yd3) 2010 5.57 18,114 114,702 9,060 57,369 2011 5.75 18,700 133,402 9,353 66,722 2012 5.91 19,220 19,220 9,613 76,335 2013 6.07 19,740 38,960 9,873 86,208 2014 6.23 20,260 59,220 10,133 96,341 2015 6.39 20,781 80,001 10,394 106,735 2016 6.55 21,301 101,302 10,654 117,389 2017 6.71 21,822 123,124 10,914 128,303 2018 6.87 22,342 145,466 11,174 139,477 (1) Estimated flows from Table 6-10. (2) Based on inert solids concentration, Xi of 90 mg/L. In Table 9-3, with the lower solids content the next biosolids removal project would be scheduled for 2011 based on a volume accumulation of 130,000 cubic yards. With the City of Marysville 9-13 Sewer Comprehensive Plan November 2011 higher solids content, the next project would be in 2018. It is recommended that the City conduct another study, similar to the ones in 1994 and 2002, to characterize actual pattern and solids content within the oxidation ponds. The estimated cost for this study is $15,000. If the biosolids removal operation is conducted when sludge accumulation reaches 20 percent of lagoon capacity, approximately 133,000 cubic yards (5,620 dry tons at 5 percent solids) will be dredged, dewatered, and hauled. In the 2003 project, 4,300 dry tons of biosolids were removed. TABLE 9-4 Cost Estimate for Contract Land Application of Class “B” Biosolids(1) Item Total Cost Permitting and Sampling $ 15,000 Contractor Mobilization/Demobilization $ 50,000 Contractor Dredging and Dewatering(2) $2,107,500 Contracted Hauling and Land Application(3) $ 252,900 Subtotal $2,425,400 Contingency (20%) $ 485,080 Subtotal $2,910,480 Sales Tax (8.5%) $ 247,390 Total Construction Cost $3,157,870 Engineering and Administrative (8%) $ 250,000 $3,407,870 (rounded) $3,400,000 (1) 2011 estimate, based on 2004 dollars. (2) Quote from Tri Max, Inc. at $377/dry ton (3) Estimate from Fire Mountain Farms at $45/dry ton In the City’s 2005 sewer comprehensive plan, the recommended schedule for biosolids removal was based on the accumulation of approximately 5,620 dry tons. Therefore, the next biosolids removal was projected for 2011 with another removal in 2018. Although the City’s Utility Model Budget projected a cost of $2,080,000 for this project in 2016, the solids have accumulated slower than previous projections. Given the slower accumulation of solids, as measured by city staff twice per year over the past five years, it is now projected that the next biosolids removal project will be scheduled for 2018 or beyond. Costs for biosolids dredging, screening, dewatering, hauling, and land application in 2018 or beyond, could easily exceed $4,000,000, given the estimates presented in Table 9-4 above, based on 2004 dollars, and including reasonable inflation factors. City of Marysville 10-1 Sewer Comprehensive Plan November 2011 CHAPTER 10 OPERATION AND MAINTENANCE INTRODUCTION This Chapter addresses the operation and maintenance of the components in the City’s sewer collection system. Those components include the pump stations and generators, force mains, and gravity pipelines. The sections of this Chapter include responsibility and authority, normal system operation, routine preventative maintenance criteria, current staffing organization and needs, capacity management operation and maintenance (CMOM) and future staffing needs, discharge policy, new construction, records, safety, and emergency response procedures. There are two primary objectives of this Chapter. The first objective is to provide documentation of satisfactory wastewater system management operations in accordance with WAC 173-230. This objective includes a description of the staff organization, existing facilities and their normal operation. The second objective of this manual is to provide an evaluation of staffing needs for existing responsibilities and new ones the City may assume in the future. These future responsibilities may include tasks associated with programs such as CMOM and the expanded collection system to serve growth. RESPONSIBILITY AND AUTHORITY The City is governed by a Mayor and seven council members. The Chief Administrative Officer reports directly to the Mayor, and oversees the management of the Public Works Department and its sewer system through the City’s Public Works Director. The organization chart for the Public Works Department is shown in Figure 10-1. There are currently a total of 87 FTEs on the Public Works staff. This department is responsible for the water system, streets, storm sewers, sanitation, the wastewater treatment plant, the sewer collection systems, and other special projects. Seven personnel are assigned to the Wastewater Treatment Plant and are responsible for the operation and maintenance of the plant and pump stations. Two lead workers and six maintenance workers are assigned to the vactor crew. Three employees from the vactor crew spend approximately 50 percent of their time flushing and cleaning the gravity sewer mains. The entire vactor crew spends about 10 percent of their time with repair and maintenance of sewer pipelines. Other tasks such as utility locates are done by water system maintenance personnel. Altogether there are approximately 15 full-time employees (FTEs) for the operation and maintenance of the wastewater treatment plant and sewer collection system. Of this number, 4 FTEs are assigned to the wastewater treatment plant and pump station maintenance. 10-2 City of Marysville November 2011 Sewer Comprehensive Plan PERSONNEL CERTIFICATION The Washington State Department of Ecology, under WAC 173-230, requires every operator in charge of a wastewater treatment plant to be certified at a level equal to or higher than the classification rating of the facility. Under condition S5 of the City’s NPDES permit, an operator certified for at least a Class III Plant shall be in responsible charge of the day-to-day operations and an operator certified for a Class II Plant shall be in charge during all regularly scheduled shifts. There are currently no Washington State certification requirements for wastewater collection system operators. However, the Department of Ecology encourages participation in a program for collection system certification. Table 10-1 summarizes the certification of staff personnel as of August 2011. TABLE 10-1 2011 Wastewater Treatment Plant Personnel Certifications Name Title Certification Level Wastewater Treatment Plant Operations Doug Byde Water Quality Manager Group IV Jeff Cobb WWTP Lead, Operations Group III Jason Crain WWTP Operator Group III Shane Freeman WWTP Operator Group II Wastewater Treatment Plant & Pump Station Maintenance Dennis Roodzant WWTP Lead, Maintenance Group II & Collection Specialist I Steven Bryant WWTP Maintenance Technician II Group I John Filori WWTP Maintenance Technician I Group I Frank Stair WWTP Maintenance Technician I Group I FULL-TIME EMPLOYEES (FTEs) Characterization of staffing often refers to full-time employees (FTEs). One FTE is defined as the equivalent manpower of one person working full time for one year. One employee may work a maximum of 2,080 hours per year. However, due to vacation days and other time off, the hours worked by one FTE is less than the maximum number of hours. Based on the City’s policies of 10 holidays, 12 sick days, two training days, and an average of 15 vacation days, one FTE is equal to 1,768 hours in 1-year. City of Marysville 10-3 Sewer Comprehensive Plan November 2011 NORMAL SYSTEM OPERATION The existing system of pump stations, force mains, and gravity lines is summarized in Tables 5-1, 5-2, and 5-3 with additional details included in Appendix C. The City’s wastewater collection system currently consists of 15 sewage pump stations, approximately 4.2 miles of force main, and 210 miles of gravity sewer line. Detailed operating instructions for pump station components are provided in the O&M Manuals for each station. The manuals have been compiled by the pump manufacturers and are on file at the wastewater facility. ROUTINE AND PREVENTATIVE MAINTENANCE CRITERIA Planning for present and future maintenance for the wastewater collection system can be considered as a task equally important to planning capital improvements or system expansion. If the maintenance effort is not expanded proportionately to system expansion, the reliability and efficiency of the system may be diminished. Goals of the maintenance program are to preserve the value of the physical infrastructure, and to ensure that all wastewater is conveyed safely, efficiently, and reliably. A planned preventative maintenance program provides the most cost-effective method for performing the optimum level of maintenance at the lowest cost. In addition to the actual maintenance tasks for system facilities, scheduling, administration, inventory, and record keeping are key components of the City’s maintenance program. The primary tasks associated with the operation and maintenance of the wastewater collection system include inspection of pump stations and generators, televising and flushing gravity sewer lines, and manhole inspection. Staffing and equipment requirements vary greatly with age, size, and type of system. For the City of Marysville, the annual budget for the operation and maintenance costs is approximately $500,000. Table 10-2 shows a more specific breakdown of actual data and costs. TABLE 10-2 2010 Operation and Maintenance Budget for Collection System Category Data Annual Budget per Mile of Sewer $2,381.00 Maintenance Dollars per Service Connection $31.32 Maintenance Workers per Mile of Sewer 0.0238 Percent of System Cleaned Annually 33 percent (target) Percent of System Video Recorded Annually 5 percent (target) 10-4 City of Marysville November 2011 Sewer Comprehensive Plan The City’s preventative maintenance (PM) program involves defining the tasks to be performed, scheduling the frequency of each task, and then providing the necessary staff to perform the task. The City’s current PM schedule for the major components of the sewer collection system is shown in Table 10-3. TABLE 10-3 Preventative Maintenance Schedule Component Visitation Schedule Maintenance Schedule Telemetry Daily • System checked daily. Gravity Sewer and Manholes Every year • Pipelines cleaned. • Video inspected as required. • Lines identified as potential problem areas are maintained on a quarterly basis. • Manholes inspected. Force Mains As necessary • As necessary. Pump Stations Weekly • Inspected 3 times per week. • Site cleaned monthly. • Wet well vactored out 2 or 4 times per year depending on station needs. Generators Weekly • Exercised automatically by the telemetry system on a weekly basis. • Fuel storage tanks are checked for fuel level and refilled monthly. • Preventative maintenance checks by in- house mechanics twice per year. • Annual services by Cummins Northwest. PUMP STATION AND GENERATOR MAINTENANCE An inventory of the mechanical equipment for each of the City’s sewage pump stations is summarized in Table 5-3. The major pieces of information recorded by City personnel, are pump run times, wet well level, running time pump amperage, and flow for major stations. Table 4-1 from the Water Environment Federation’s (WEF) Manual of Practice 7, Wastewater Collection Systems Management provides an extensive list, of the tasks associated with preventative maintenance at pump stations. Some of these tasks may not be required as frequently, if at all, at some of the smaller pump stations. An abbreviated table, Table 10-4, covers maintenance items for the City’s larger wet well/dry well pump stations. City of Marysville 10-5 Sewer Comprehensive Plan November 2011 TABLE 10-4 Pump Station Maintenance Schedule Item Weekly Monthly Quarterly Yearly Pump Station Write down hours Check pump cycle counter Check wet well ventilation Check for leaks in dry well Check sump pump Check telemetry in pump stations Clean Floats Clean and sanitize dry well Drain air Compressors Clean out Drain Sumps Pump out and clean wet well Grease all pumps Clean check valves Paint interior and piping (5 years) Check all force mains that discharge to manholes Check all Electric panels Inspect pump impellers Twice Per Year Use portable generator to test transfer switches and proper electrical transfer at stations without onsite generators. Generators Test Run Exercise Check oil Check coolant level Check and top off fuel level Twice Per Year Check oil filter Check air filter Check battery fluid level and fan belts Check battery terminals for corrosion Check alternator output volts Check RPM Pump station staffing requirements vary greatly depending on the size and complexity of the station as well as the scheduled maintenance routine. Inspection and maintenance staffing needs typically range from 0.052 to 0.42, and 0.07 to 0.63 FTEs per pump station, respectively. Combining both tasks results in a range of 0.12 to 1.05 FTEs per pump station. 10-6 City of Marysville November 2011 Sewer Comprehensive Plan The City has three of its staff assigned to mechanical inspection of equipment at the wastewater treatment plant and the pump stations. Each pump station is physically inspected three times per week. The auxiliary generators are exercised and checked weekly. Assuming a 50 percent allocation to pump station inspection and maintenance, approximately 1.5 FTEs are assigned full-time to pump station maintenance. In addition to the regularly scheduled inspections, the vactor crew pumps out each wet well 2 to 4 times per year, depending on the specific needs at each station. This work adds 0.2 FTE to pump station maintenance. With an additional 0.3 FTE for supervision (20 percent of the maintenance lead’s time), the City’s total for pump station O&M is 2.0 FTEs. The City’s pump stations can be organized into two groups based on maintenance requirements. Its smaller development type pump stations include Carrol’s Creek, Regan Road, Cedar Crest Vista, 3rd Street, Kellogg Ridge, Quilceda Glen, Ash Avenue, Eagle Bay, and the Waterfront Park pump stations. These pump stations are equipped with small horsepower motors and do not have onsite auxiliary generators (with the exception of Regan Road, which has an onsite generator). All of the stations are equipped with an emergency generator plug that adapt to the City’s portable generator. A staffing value of 0.12 FTE is assigned to each of the small pump stations. The City’s primary pump stations include Soper Hill, 88th Street, Marysville West, 51st Avenue, Sunnyside, and West Trunk. These six pump stations are equipped with larger horsepower pumps and auxiliary generators (except Marysville West). In addition, two of these pump stations, 51st Avenue and Sunnyside, have three pumps instead of the standard of two found at other stations. It is assumed that the City’s six primary pump stations require on average, 40 percent more manpower than the smaller pump stations. A staffing level of 0.17 FTEs is assigned to each of the primary pump stations due to their complexity and additional equipment. Table 10-5 summarizes the estimated staffing requirements for the City’s pump stations based on the two categories. The minimum recommended staffing level for the City’s 15 pump stations is 2.10 FTEs, which is only slightly greater than the current staffing level of 2.0 FTEs. Based on the existing number of pump stations, the City’s staffing is adequate for routine, preventative maintenance. TABLE 10-5 Pump Station Inspection and Maintenance Staffing Requirements Category Number Employees Per Total Employees Developer 9 0.12 1.08 Primary 6 0.17 1.02 Total 15 2.10 FTEs City of Marysville 10-7 Sewer Comprehensive Plan November 2011 GRAVITY SEWERS AND MANHOLES The major maintenance activities with respect to gravity sewers and manholes are periodic inspection and flushing. The older portions of the City’s sewer collection system should be given special attention because of the potential for breaks in sewer lines or accumulated solids in these areas. For the City of Marysville, the older sewers are located in the neighborhood areas of Downtown, Cedar Crest, and Jennings Park. In addition, sewers with minimum grade require more frequent cleaning. These sewers were identified from the results of the hydraulic model and are shown in Appendix E and Exhibit VI. City staff has made cleaning its gravity sewers a priority with a goal of flushing its sewer system every two and a half years. This frequency is supported by the results of the hydraulic model, which showed that 45 percent of the modeled trunk sewers had pipeline velocities less than 2 fps. PIPELINE CLEANING Periodic cleaning of the sewer collection system will ensure that sewers remain clear of blockages and free of odors. Root intrusion, grease, and deposited solids are the most common cleaning problems. Root intrusions develop through deteriorated joints or broken pipe. Over time, roots cause restrictions in the pipeline, which may cause system backups. Grease buildup in a pipe results from waste oils from commercial and residential food preparation. Grease floats to the surface and coats the inside of the pipe. Repeated coatings harden over time and may constrict the pipe diameter to a fraction of its original size. Deposit of solids result from low flow pipelines or low pipeline velocities. To maintain minimum scouring in pipelines, a velocity greater than 2-feet per second is required. However, because of minimum slope, low flow, and misaligned joints, this minimum velocity is not always achieved and solid material has an opportunity to deposit in the pipe channel. There are several methods available for pipeline cleaning: hydraulic, mechanical, and chemical. Each one is described below. HYDRAULIC CLEANING Hydraulic cleaning refers to any application of water to clean the pipe. Typically, the hydraulic unit is either trailer or truck mounted and has various sizes of water tanks and different types of power drives. A water pump delivers water through a nozzle at a high pressure and volume moving most materials in a pipe. The newest development in high velocity cleaning is the addition of vacuum systems to form a combination cleaner. This system employs the same cleaning techniques as high velocity cleaners but also use a vacuum to remove material from the pipe. A positive 10-8 City of Marysville November 2011 Sewer Comprehensive Plan displacement or air pump is used to generate the vacuum. Water from the collected material can be siphoned off and returned to the sewer system. MECHANICAL CLEANING Power rodding equipment is utilized to remove blockages in sewer pipelines such as those caused by root intrusion or grease accumulations. The rod, which is stored on a reel, is fed into the line and turned on automatically. Rodding machines can be trailer or truck-mounted and are available with various engine sizes and a wide array of rod diameters and lengths. Rodders are often used in conjunction with high velocity hydraulic cleaners to first remove debris. Then, the rodder is used to remove the blockage. For follow-up action, the high velocity cleaner should be used periodically to prevent future buildup and blockages. The location of all blockages should be mapped and used for the cleaning program. CHEMICAL CLEANING Chemical treatment can be used for root and grease control. Chemical products such as copper sulfate and sodium hydroxide may kill roots with repeated applications but do not necessarily inhibit regrowth. Typically, roots would first be removed by mechanical means and then herbicides applied to prevent regrowth. Herbicides can inhibit growth for two to seven years. Chemical additives are also available for grease control. Agents such as bacterial cultures, enzymes, hydroxides, caustics, bioacids, and neutralizers are available to help control severe grease buildups but require regular application. Chemical applications for root and grease control are recommended only as a last resort. These applications may negatively impact the operation of the treatment plant or simply transfer a problem to a downstream location. However, in limited access or high-traffic areas where set-up of cleaning or rodding machinery may be difficult, chemicals may be the only viable solution. VIDEO INSPECTION Inspection by closed circuit television is the most effective method of determining the nature and extent of internal problems in the sewer collection. The video inspection can locate misaligned joints, broken and cracked pipe, pipeline intrusions, and other structural defects. Particularly where older pipe is in service, a record of structural defects is required for establishing a pipeline rehabilitation program. When structural defects are found, open cut and replacement is required. If the pipeline contains deteriorated joints but is otherwise in good condition, trenchless means for pipeline rehabilitation are an available alternative. The current range of inspection is almost unlimited. Small cameras can inspect even 4-inch service laterals, so long as a suitable cleanout is available for access. Also as with rodding equipment, video inspection equipment is often utilized with hydraulic cleaning. City of Marysville 10-9 Sewer Comprehensive Plan November 2011 Video inspection equipment will not operate well in pipelines with debris and gravel accumulation. CLEANING AND INSPECTION STANDARDS There is no well established industry standard for cleaning and inspection intervals. Cleaning is typically performed more often than inspection and varies between 25 and 40 percent of the system per year. Cleaning is performed more often than inspection because it addresses the accumulation of debris which can cause hydraulic disruptions in a short period of time. Inspection, on the other hand, identifies deteriorated or damaged structures due to corrosion, root penetration, or soil shifting which occur at a relatively slow, albeit consistent rate. At this time the City will continue to place emphasis on cleaning as compared to video inspection. System goals are 40 percent for cleaning and 5 percent for video inspection. Typical rates of inspection and cleaning vary from 12 to 97, and 29 to 932 feet per hour. Table 10-6 estimates the staffing requirements for the current system. An inspection and cleaning rate of 50 and 250 feet per hour, respectively, is used as the basis for the calculations. The results in Table 10-6 show 2,900 crew hours per year, or 3.2 FTEs. TABLE 10-6 Staffing Requirements for Inspection and Cleaning Length of Gravity Pipe (miles) Target Interval (years) Length per Year (feet) Rate per Crew (ft/hour)(2) Required Number of Crew Hours Video Inspection 210 20 55,000 50 1,100 Pipeline Cleaning 210 2.5 450,000 250 1,800 Total 2,900 hrs/yr(1) (1) 2,900 hrs/1,768 hrs/FTE x 2 FTEs/Crew=3.2 FTEs (2) Annual basis. CURRENT STAFFING NEEDS Based on the estimated staffing requirements for the City’s pump stations and gravity sewers (Table 10-6), the total staffing requirements for the existing collection system is 5.3 FTEs, slightly more than the number of staff currently assigned (5.0 FTE’s). FUTURE STAFFING NEEDS The unit rates for pump station maintenance and gravity sewer cleaning and inspection can be used to estimate future staffing needs. As the sewer system expands, the operation 10-10 City of Marysville November 2011 Sewer Comprehensive Plan and maintenance requirements will expand accordingly. Growth in the collection system is based on the area covered by the sewer system. This basis is more representative than population since it recognizes some “in-fill” (therefore no growth in the sewer collection) and also an expansion of the area served (therefore, additional requirements to maintain new sewer mains). Table 10-7 presents an estimate of the future staff needs based on the expected number of new pump stations and the future size of the gravity sewer system through the year 2025. TABLE 10-7 Estimation of Future Staffing Needs Collection System Year 2010 2017 2031 Estimated Sewer Service Area (Ac)(1) 4,979 5,708 7,340 Miles of Sewer 210 240 310 Number of Pump Stations(2) 15 16 19 Gravity System FTEs 3.2 3.7 4.8 Pump Station FTEs 2.1 2.2 2.7 Total Maintenance FTEs 5.0 5.9 7.0 (1) Table 6-10. (2) One pump station by 2017 in Whiskey Ridge. Based on the analysis presented in Table 10-7, the City’s staffing needs for the collection system are expected to increase by 0.9 FTEs by 2017 and 2.0 FTEs by 2031. An additional FTE should be added in 2017, followed by one more additional FTE by 2031. CAPACITY MANAGEMENT OPERATION AND MAINTENANCE (CMOM) AND FUTURE STAFFING NEEDS Capacity Management Operation and Maintenance (CMOM) This Section evaluates staffing requirements for new responsibilities the City may assume under the proposed Capacity Management Operation and Maintenance (CMOM) regulation by the Environmental Protection Agency. The legal basis for the CMOM regulation is that nearly all collection systems have unplanned releases at sometime and that these releases are regulated under the jurisdiction of the Clean Water Act. The purpose of CMOM regulations is to ensure that collection systems are operated and maintained with the same level of attention that treatment plants receive. The regulation has been issued only in draft form and it is uncertain when the final regulation will be issued. The draft regulation contains several requirements regarding the operation of the sewer collection system. The City currently addresses most of the proposed requirements City of Marysville 10-11 Sewer Comprehensive Plan November 2011 through its normal operations or studies, which it has authorized in recent years. However, other requirements may represent new responsibilities, which have not previously been part of the City’s normal operation. Each of the draft regulatory requirements under CMOM is presented below along with a brief discussion of how the City is or will need to address each one. Those items, which are not currently included in the City’s normal operation, are discussed in more detail with the impact to City staffing. CAPACITY MANAGEMENT OPERATION AND MAINTENANCE (CMOM) DRAFT REQUIREMENTS 1. Meet additional general sewer system performance standards including up to date system maps, information management systems, and odor control requirements. The City has an up-to-date sewer basemap and a geographical information system (GIS) and a set of Developer Standards to ensure the consistency and quality of sewer construction. The City’s sanitary sewer design standards are reviewed and revised on a regular basis. A major step towards preventing problems within the sewer collection system is proper installation at the time of construction. The City has adopted Developer Standards pertaining to the sanitary sewer system. These standards are continually reviewed and updated by engineering and maintenance personnel. Standard designs should be developed to minimize total life cycle costs, which include capital, O&M, and financing costs. Also, as the system becomes more complex, special attention should be given to its ability to function during emergency situations. 2. Maintain program documentation including the goals, organization, and legal authority of the organization operating the collection system. The City has well defined lines of authority for the operation of its sewer collection system. The organizational chart is presented in Figure 10-1. 3. Develop an overall response plan that can respond to releases in less than 1 hour and is demonstrated to have sufficient personnel and resources. The City has an emergency response plan in place. 4. Plan for system maintenance, evaluation, and replacement requirements mandating that the collection system be cleaned on scheduled basis, be regularly video inspected, and develop a short- and long-term program for pipeline replacement and rehabilitation. 10-12 City of Marysville November 2011 Sewer Comprehensive Plan The City has a full-time vactor crew with a target goal of cleaning 50 percent of its sewer system each year. In addition, Exhibit VI of this Plan shows the location of trunk sewers with low pipeline velocities, the priority areas for cleaning. Over the past several years the city has budgeted for annual sewer pipeline renewals and replacements. In 2011, due to budget constraints, no monies were budgeted for renewals and replacements. The city plans to continue budgeting for this in future years. 5. Plan for controlling Fats, Oils, and Grease (FOG) that increases in incidences of SSOs. The City of Marysville has an effective FOG program under the City’s Muncipal Code 14.20, wastewater pretreatment. The City maintains a database of all of its FOG dischargers, including dates for next and last inspections, last cleaned, type of FOG device, and general condition of system. All dischargers are required to complete and submit a cleaning maintenance log for the City’s records. 6. Develop a capacity assurance and management plan with flow meters to model Infiltration and Inflow (I/I) and system capacity. The City has flow meters installed at its wastewater treatment plant and 51st Avenue, Soper Hill and Sunnyside Pump Stations. In addition, the City completed an I/I study in 1999. To date, however, the available data has not successfully characterized I/I by individual basins or specific sections of the sewer collection system. Based on average annual flow data, I/I accounts for approximately 20 percent of the plant flow. 7. Develop a self-audit program to evaluate and adjust performance. The City maintains detailed records at its wastewater treatment plant and pump stations. The City has the capability of determining the success of any pipeline replacement or rehabilitation program through its historical plant flow records and flow meter located at the main pump stations. The City will need to implement a program for compiling and evaluating these records and implementing a system for system maintenance based on identified and reoccurring problem areas. 8. Develop a program to communicate information on problems, costs, and improvements to the public and decision-makers. Along with the CMOM program, EPA has provided a self assessment checklist which can be utilized to identify areas of strength and weaknesses of utility operations. A copy of this checklist is included in City of Marysville 10-13 Sewer Comprehensive Plan November 2011 Appendix G. This checklist should be updated periodically to provide a comparison of performance over time. The City has consistently updated its Sewer Comprehensive Plans and prepared facility plans specifically to identify problems, develop costs for improvements, and inform the decision-makers. The City conducts regularly scheduled public meetings and sends out brochures informing the public of project updates. The City will need to periodically provide information to the public on the number of sewer spills and backups during the year and explain the City’s short and long term response to these incidents. SAFETY An important consideration of any successful maintenance program is the safety and well being of all employees. The City’s safety program addressing accidents, fall protection, confined spaces, and lockout/tagouts are based on the standards of the Washington State Department of Labor and Industries (L&I). The safety program addresses the situations that employees may encounter during the performance of operation and maintenance tasks. Field employees meet weekly for safety meetings, which include training and discussion of safety issues. The following section includes applicable recommended and required safety provisions for confined spaces, electrical and mechanical equipment, fire hazards, and health hazards. CONFINED SPACES The principle hazards associated with confined spaces, including wet wells, sewer manholes, and pump stations, are oxygen deficiency, explosions, and toxic gases. Oxygen deficiency occurs whenever air is displaced by some other gas, which may or not be toxic. L&I has established regulations governing entrance into confined spaces in WAC 296-62-145. The regulations include the completion of a Confined Space Entry Permit, the establishment of Safe Operating Procedures, and the completion of a Confined Space Pre-Entry Checklist. A minimum of two individuals is required when any work is to be accomplished within pump stations, wet wells, or sewer manholes. A gas monitor is required for measuring oxygen levels, explosion potential (LEL), and toxic gases. The gas monitor must be used to continually monitor gas levels while any person is within the confined space. Rapid changes in gas levels can occur in sewage effluent due to upstream spills or discharges, and result in rapid atmospheric changes. The gas monitor will sound an alarm if a critical level for a measured gas is reached. 10-14 City of Marysville November 2011 Sewer Comprehensive Plan A portable air blower should be available to the operator whenever work in manholes or wet wells is performed. The air blower can be used to provide ventilation in confined spaces, but the motor should be kept away from the opening to the space to avoid the ignition of explosive gases that may be present and to keep carbon monoxide from entering the confined space, creating a dangerous situation. City confined space procedures should be reviewed with maintenance personnel on a regular basis and revised as new regulations and equipment evolve. ELECTRICAL AND MECHANICAL EQUIPMENT The presence of electrical mechanical equipment at the pump stations may present hazards to personnel during the performance of operation and maintenance tasks. Precautions should be taken whenever working on or near the pump station mechanical and electrical equipment. Rubber mats should be placed on the floor in front of all electrical control panels. When working on any piece of electrical equipment, the operator should ensure that all switches are opened and tagged, all electrical equipment is grounded, and all exposed wire is taped. All portable power tools, extension cords, and lights should be of the three-wire grounding type. Exposed shafts and belts are hazardous items of mechanical equipment that can be found in pump stations. Belts and shafts should be enclosed in sheet metal or wire guards. When work is being conducted on any piece of equipment with exposed shafts or belts, the item of equipment should be taken off line so that it will not start. Other safety precautions that should be observed by City personnel are to avoid contact with energized circuits or rotating parts, to avoid bypassing or rendering inoperative any safeguards or protective devices, and to avoid extended exposure in close proximity to machinery with high noise levels. City of Marysville 10-15 Sewer Comprehensive Plan November 2011 FIRE HAZARDS Fires are possible in any area of a pump station if debris is allowed to accumulate. Precautions should be taken to reduce the possibility of a fire. Oily rags should be kept in a tightly sealed metal can, preferably at a location away from the pump station. All areas should be kept free of clutter or debris, especially if flammable in nature. Gasoline or solvents should only be used in well-ventilated areas, away from sources of ignition. A carbon dioxide type, dry chemical, or foam fire extinguisher should be permanently mounted at each pump station. The extinguisher should be tagged and checked semi- annually to ensure that it is operational. HEALTH/SAFETY The possibility exists that any particle of wastewater may contain disease-causing bacteria. Operators should take precautions to avoid disease at all times. Principle water- borne diseases include typhoid fever, dysentery, Giardia, Cryptosporidium, infectious jaundice, and tetanus. Immunization against some of the diseases is possible and all operators should be vaccinated periodically. Operators should take individual precautions to avoid disease, including the following: • Keep hands below collar when working at sewer facilities • Wear rubber gloves whenever directly handling sewage • Disinfect hands with hot water and soap or antibacterial location before eating • Treat minor cuts and wounds immediately Additionally, emergency first aid kit should be kept in each City vehicle and other convenient locations, so as to be readily available to operators. EMERGENCY RESPONSE The operation of the sewer system under emergency conditions is an important responsibility of the City’s staff. Emergency response procedures should be rehearsed and reviewed by personnel. An overview of the potential effects and recommended actions for emergency situations is presented in Tables 10-8 and 10-9. The five emergency situations considered are power loss, flooding, hazardous waste spill, earthquake, and sabotage/vandalism. The potential effects and recommended actions are identified for sewage pump stations, force mains, and the gravity sewer system. The City has established an emergency response plan. Also, field staff is trained in established procedures for after-hours and emergency service calls. 10-16 City of Marysville November 2011 Sewer Comprehensive Plan TABLE 10-8 Emergency Response Actions for Pump Stations Emergency Pump Stations Potential Effects Recommended Actions Power Loss Pumps rendered inoperable, auxiliary generators activated to run pumps. Transport portable generators to pump stations that do not have auxiliary power, check other pump stations to ensure generators are operating. Flooding Station overflow. Use Pumper Trucks to move sewage until flooding effects subside. Hazardous Waste Spill Spill enters wet well at a pump station. Isolate pump station receiving spill, pump out of wet well and dispose of hazardous materials, notify Snohomish County, DOH, and DOE of situation. Earthquake Wet well damaged, inlet and outlet piping severed or damaged. Use Pumper Trucks to move sewage while repairs are made. Sabotage/Vandalism One or more pumps rendered inoperable. Isolate damaged pump(s) and operate other pumps while repairs are made. TABLE 10-9 Emergency Response Actions for Force Mains Emergency Pump Stations Potential Effects Recommended Actions Power Loss No anticipated effects No actions anticipated Flooding No anticipated effects No actions anticipated Hazardous Waste Spill No anticipated effects No actions anticipated Earthquake Breaks in force main pipes Implement bypass pumping at critical areas. Sabotage/Vandalism Force mains plugged or broken Isolate damaged area, implement bypass pumping until affected area is repaired. City of Marysville 10-17 Sewer Comprehensive Plan November 2011 TABLE 10-10 Emergency Response Actions for Gravity Sewer Emergency Pump Stations Potential Effects Recommended Actions Power Loss No anticipated effects No actions anticipated Flooding Manholes surcharged Implement bypass pumping at critical areas. Hazardous Waste Spill Spill enters sewer system Isolate pump station receiving spill, pump out of wet well and dispose of hazardous material, notify Snohomish County Health, and DOE of situation. Earthquake Breaks in sewer lines. Damaged manholes Isolate damaged area, implement bypass pumping until affected area is repaired. Sabotage/Vandalism Gravity sewers plugged or broken. Manholes damaged Isolate damaged area, implement bypass pumping until affected area is repaired. MAINTENANCE PERSONNEL QUALIFICATIONS A well-trained staff is an essential part of an effective operation and maintenance program. Maintenance personnel should be familiar with current equipment and procedures, as well as all applicable regulations. Training criteria should be established for each job description and reviews conducted accordingly. Training activities should be considered to be as important as any other maintenance activity and should be included and budgeted into the regularly scheduled tasks. The City regularly budgets for training. In 2011, the City budgeted $8,000 for travel and training of its collection system and wastewater treatment plant personnel. City of Marysville 11-1 Sewer Comprehensive Plan November 2011 CHAPTER 11 CAPITAL IMPROVEMENT PLAN INTRODUCTION This Chapter presents a 6-year Capital Improvement Plan (CIP) in accordance with the requirements of WAC 173-240 as well as a 20-year CIP. Wastewater system capital improvements have been scheduled and prioritized on the basis of growth, regulatory requirements, component reliability, system benefit, and cost. Location maps for the collection system and wastewater treatment plant CIP improvements are presented on Figure 11-1. For each capital improvement project, detailed project descriptions and preliminary project cost estimates are provided. Each project cost estimate includes design and engineering, construction with a 20 percent contingency, 8.6 percent state sales tax, and construction management. Costs are based on 2010 construction dollars. Selected cost estimates are presented in Appendix H. The required capacity and timing of each recommended improvement is provided for budgeting and financial projection purposes only. The actual design parameters should be evaluated at the design phase of the project, using the hydraulic model or another accepted engineering procedure. Updated population and flow data should be used when available to ensure that the proposed facilities are adequately sized to handle build-out flows. The City regularly updates its 6-year CIP project list and currently has a 6-year list extending from 2011 to 2017. The development of this Plan confirmed several of the CIP projects, which were already scheduled. The revised 6-year CIP begins with the year 2012 and extends through 2017 as shown in Table 11-1. The City’s CIP projects for 2011 are included in Table 11-1 for reference. Future projects that are not identified as part of the City’s CIP presented in this Chapter may become necessary. Such projects may be required in order to remedy an emergency situation, to address unforeseen problems, or to accommodate improvements from adjacent jurisdictions. Due to budgetary constraints, the completion of such projects may require modifications to the recommended CIP. The City retains the flexibility to reschedule, expand, or reduce the projects included in the CIP and to add new projects to the CIP, as best determined by the Council, when new information becomes available for review and analysis. SS-D 71st St NE Sewer Upsizing 64th Ave NE to 66th Ave NE SS-C Whiskey Ridge Sewer Extension Gravity Main SS-E Trunk G Rehab Cedar to Columbia PS-B West Trunk Pump Station Upsizing PS-A Whiskey Ridge Sewer Pump Station & Force Main PS-C Carroll's Creek Pump StationEmergency Generator Installation PS-D Cedarcrest Vista Pump StationEmergency Generator InstallationI-5SR 967TH AVE NESTATE AVESR 9251ST AVE NESR 529GROVE ST 83RD AVE NE27TH AVE NE64TH ST NE 84TH ST NE 108TH ST NESMOKEY POINT BLVD152ND ST NE MARINE DR140TH ST NE SUNNYSIDE BLVD99TH AV NE47TH AVE NE4TH ST 100TH ST NE 88TH ST NE CEDAR AVE116TH ST NE 8TH ST FORTY-FIVE RD 172ND ST NE BEACH AVE136TH ST NE 44TH ST NE 132ND ST NE 71ST AVE NE3RD AVE NE80TH ST NE ASH AVE34TH AVE NE48TH DR NE140TH ST NW FORTY FIVE RD 40TH ST NESHOULTES RD1ST ST 76TH ST NE M AR IN E D R N E 52ND ST NE 99TH AV NEI-534TH AVE NE172ND ST NE 51ST AVE NE88TH ST NE 51ST AVE NE84TH ST NE 132ND ST NE 2011 Six Year CIP Pump Stations 2011 Six Year CIP Lines71st St NE Sewer Upsizing 64th Ave NE to 66th Ave NE Trunk G Rehab Cedar to Columbia Whiskey Ridge Sewer Extension Force Main Whiskey Ridge Sewer Extension Gravity Main Urban growth area 0 2,000 4,000 6,0001,000 Feet Sewer Comprehensive Plan Figure 11-1 Six Year CIP 11-2 City of Marysville November 2011 Sewer Comprehensive Plan PROPOSED SYSTEM IMPROVEMENTS FROM 2011 TO 2017 The recommended CIP projects are summarized using the existing City descriptions: • Sanitary sewer mains (SS) • Pump stations (PS) • WWTP improvements (WWTP) • General system improvements (GS) After a brief description for each CIP category, each CIP project is described with use of a lettered subscript, “a,” “b,” etc., and a total project cost is presented. SANITARY SEWER MAINS The results of the hydraulic model for 2010, 2017, and 2031 indicated 118 pipeline capacity deficiencies. Eliminating or preventing surcharged pipelines is the priority of the recommended CIP improvements for the sewer system. The impact on the numerous surcharged pipelines in Trunk F will be lessened when the Lakewood Sewer Extension Project – Phase II is constructed and flow is diverted to this new pipeline. Numerous surcharged manholes were identified in the model. However, a number of these surcharges were determined to be insignificant enough to warrant a 6-year capital improvement project. These areas were analyzed in a separate memorandum to the city and are not included in the following CIP plan. The following projects are intended to be a part of the 6-year CIP. Other pipeline deficiencies identified by the hydraulic model are included in the 20-year CIP. City of Marysville 11-3 Sewer Comprehensive Plan November 2011 6-YEAR CIP (2012 – 2017) SS-a: SEWER MAIN OVERSIZING The City has budgeted an annual amount to cover the costs of oversizing sewer mains for various developer extension projects. Estimated Project Cost: ......................................................................... $30,000 annually SS-b: RENEWALS AND REPLACEMENTS The City has budgeted an annual amount beginning in 2013 to cover renewals and replacements of 8-inch or less pipe within its sewer system. Estimated Project Cost: ........................................................................ $300,000 annually SS-c: WHISKEY RIDGE SEWER EXTENSION (2012) This project extends gravity sewer east on Soper Hill Rd from 200-feet west of 83rd Ave NE to Densmore Rd and north on Densmore Rd to the approximate intersection of State Route 92. The project includes construction of 4,300 linear feet of 12-inch gravity sewer. Estimated Project Cost: ....................................................................................$ 1,200,000 SS-d: 71ST ST NE SEWER UPSIZING – 64TH AVE NE to 66TH AVE NE (2015) At 64th Avenue and approximately 71st Street, an existing 18-inch sewer is connected to a 12-inch sewer. Modeling results show surcharging upstream of this connection. To ensure future capacity, 510 linear feet of 18-inch gravity sewer will replace existing 12-inch sewer. Estimated Project Cost: .......................................................................................$ 410,000 SS-e: TRUNK “G” REHABILITATION - CEDAR TO COLUMBIA (2016) This project includes some of the City’s older pipelines and includes rehabilitation and replacement of approximately 415 linear feet of 15-inch gravity sewer and 1,000 linear feet of 21-inch sewer, including pipe located just east of the Burlington Northern crossing. The pipe will be replaced with 1,415 linear feet of 24-inch PVC. In addition, the slope of 580 LF of 24-inch pipe downstream of the existing 21-inch shall be revised to a more consistent slope of 0.0029 to remove a known sag in the pipe. Estimated Project Cost: .....................................................................................$1,340,000 11-4 City of Marysville November 2011 Sewer Comprehensive Plan PUMP STATIONS City staff has indentified one of its pump stations (West Trunk) that will have a flow deficiency by 2017. Of the four pump station projects, which the City has included in its CIP, only the West Trunk project is due to a deficiency in the system. The other three projects included, the Whiskey Ridge pump station and force main, which is a new installation being made to accommodate growth in the Southeast section of the city, and the Carroll’s Creek and Cedarcrest Vista pump station generator installations are proactive improvements to reduce risk to the city during prolonged power outages. PS-a: WHISKEY RIDGE SEWER PUMP STATION AND FORCE MAIN (2014) A sewer pump station will be constructed along Densmore Rd. near the intersection of Densmore Rd and Sunnyside School Rd to accommodate growth in the East Sunnyside/Whiskey Ridge subarea. Additionally, 1,500 lineal feet of 4-inch diameter force main will be installed along Densmore Rd. to south of SR 92 where it will enter a 12-inch gravity line that is intended to be installed in 2012. Estimated Project Cost: .....................................................................................$1,000,000 PS-b: WEST TRUNK PUMP STATION – PUMP UPSIZING (2013) Larger pumps, and improvements to wiring and controls will be installed to maintain adequate capacity at the pump station. The improvements are scheduled for 2013. Estimated Project Cost:……………………………………………………….$225,000 PS-c: CARROLL’S CREEK PUMP STATION EMERGENCY GENERATOR INSTALLATION (2016) An emergency generator, proper wiring, and automated transfer switch will be installed at the pump station, to provide power to the station during prolonged power outages. Estimated Project Cost:………………………………………………………$175,000 PS-d: CEDARCREST VISTA PUMP STATION EMERGENCY GENERATOR INSTALLATION (2017) An emergency generator, proper wiring, and automated transfer switch will be installed at the pump station, to provide power to the station during prolonged power outages. Estimated Project Cost:………………………………………………………$175,000 City of Marysville 11-5 Sewer Comprehensive Plan November 2011 WWTP IMPROVEMENTS Several projects and improvements are included in the City’s CIP for the wastewater treatment plant. The most significant costs are for biosolids removal, which is not anticipated to be completed until 2018 or beyond, however the city has allocated $300,000 from 2014 through 2017 to help defer the cost of the project, which is estimated at $3.4 million. In addition, due to the difficulty in predicting the schedule for biosolids removal, a preliminary biosolids profile is scheduled for 2016. The profile will help the city determine sludge depth, location, quantities, solids concentration, classification, and need for scheduling the removal. Other scheduled improvements include replacement or reconstruction of the headworks parshall flume, extension of the filter reject line to complete mix cell 1 at the headworks of the plant, upsizing the filter reject pump station wet well and pumps, construction of a pre-settling basin, and replacement of the mechanical barscreens at the headworks. A flow study listed for 2013 is intended to better identify I/I in the collection system. The results of the flow study can be used to refine the hydraulic model by identifying I/I in individual basins. Another project that is currently underway and anticipated to be completed before the end of 2011, is the installation of an onsite generator at the wastewater treatment plant. The generator is intended to power the effluent side of the plant and the laboratory building during prolonged power outages in the future. WWTP-a: BIOSOLIDS REMOVAL (2018 or Beyond) This part of the CIP covers an annual amount for future biosolids removal projects. The next project in 2018 is estimated to cost $3.4 million. Estimated Project Cost……………………... annually beginning in 2014 - $300,000 WWTP-b: REPLACEMENT/RECONSTRUCTION OF HEADWORKS PARSHALL FLUME (2013) Replacement or reconstruction the concrete influent parshall flume at the headworks of the plant, or to install a fiberglass insert to correct the current deficiencies in the flow measurement there. The existing concrete structure would need to be resurfaced and leveled. Estimated Project Cost: ..........................................................................................$50,000 11-6 City of Marysville November 2011 Sewer Comprehensive Plan WWTP-c: EXTENSION OF THE FILTER REJECT LINE TO COMPLETE MIX CELL 1A (2013) Extension of the filter reject line from the West Trunk Pump Station to Complete Mix Cell 1A at the Headworks of the WWTP. Estimated Project Cost: ........................................................................................$100,000 WWTP-d: UPSIZING OF THE FILTER REJECT WET WELL AND PUMP SYSTEM (2014) This project would construct a larger wet well, upsize to larger pumps, and make improvements to wiring, controls, and telemetry at the station. Estimated Project Cost: ........................................................................................$500,000 WWTP-e: PRE-SETTLING BASIN PRIOR TO EFFLUENT FILTRATION (2015) This project would construct a pre-settling basin to allow flocculation and settling prior to effluent filtration. Estimated Project Cost: .....................................................................................$1,000,000 WWTP-f: SCREEN REPLACEMENT FOR MECHANICAL SCREENS (2017) Both of the City’s mechanical screens have bar spacings of 1 ½ inches, which allows a significant amount of debris to pass through to downstream processes such as the effluent filters and effluent pumps. The proposed project would replace these screens with ones with bar spacings of 3/8 inch or less. Estimated Project Cost: ........................................................................................$500,000 WWTP-g: FLOW STUDY (2013) The purpose of the proposed flow study is to monitor flow at different locations within the City’s collection system to provide better information about the extent and location of infiltration/inflow. The available information indicates that parts of the upper Trunk A and Trunk CE systems are two areas with higher than normal infiltration/inflow. Estimated Project Cost: ..........................................................................................$40,000 City of Marysville 11-7 Sewer Comprehensive Plan November 2011 WWTP-h: PRELIMINARY BIOSOLIDS PROFILE (2016) This project is one of the preliminary steps to determine the schedule for the next biosolids removal project from the City’s lagoons. The work would include an evaluation of the accumulation of biosolids by location, depth, and solids content. Based on this data, the City can estimate the rate of biosolids accumulation since 2003 and when the next project will be required. Estimated Project Cost: ..........................................................................................$12,000 WWTP-i: WASTEWATER TREATMENT PLANT GENERATOR (2011) This project is currently in progress and scheduled for completion by the end of 2011. The work includes installation of an emergency generator, wiring, transfer switches, controls, and telemetry to power essential buildings and equipment at the effluent side of the wastewater treatment plant during prolonged power outages. Estimated Project Cost:…………………………………………………………$400,000 GENERAL SYSTEM IMPROVEMENTS The proposed general system improvements for 2012 – 2017 include a cost of service study (2016), an update for the sewer comprehensive plan (2017) and a sewer rate study (2013). TOTAL 6-YEAR CIP The total amount for the 6-year CIP (2012 – 2017) for all of the projects listed in Table 11-1 is $10,207,000. The total amount includes the following amounts for each category: Sanitary Sewer Mains ..................................................................$4,630,000 Pump Stations ............................................................................$ 1,575,000 WWTP Improvements ...............................................................$ 3,402,000 General System Improvements ..................................................$ 600,000 Total ..........................................................................................$10,207,000 City of Marysville 11-8 Sewer Comprehensive Plan November 2011 TABLE 11-1 6-Year Capital Improvements Plan(1) 2011 2012 2013 2014 2015 2016 2017 Sanitary Sewer Mains a. Sewer Main Oversizing $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 b. Renewals and Replacement $300,000 $300,000 $300,000 $300,000 $300,000 c. Whiskey Ridge Sewer Extension $200,000 $1,200,000 d. 71st St NE Sewer Upsizing: 64th Ave NE to 66th Ave NE $410,000 e. Trunk “G” Rehab.: Cedar to Columbia $1,340,000 Total Sanitary Sewer Mains $230,000 $1,230,000 $330,000 $330,000 $740,000 $1,670,000 $330,000 Pump Stations a. Whiskey Ridge Sewer Lift Station and Force Main $1,000,000 b. West Trunk Pump Station Upsizing $225,000 c. Carroll’s Creek Pump Station Emergency Generator Installation $175,000 d. Cedarcrest Vista Pump Station Emergency Generator Installation $175,000 Total Pump Stations $0 $0 $225,000 $1,000,000 $0 $175,000 $175,000 (1) The 6-year CIP covers the period of 2012 - 2017. 2011 CIP projects are included for reference. City of Marysville 11-9 Sewer Comprehensive Plan November 2011 TABLE 11-1 – (continued) 6-Year Capital Improvements Plan(1) 2011 2012 2013 2014 2015 2016 2017 WWTP Improvements a. Biosolids Removal $300,000 $300,000 $300,000 $300,000 b. Replacement/Reconstruction of Headworks Parshall Flume $50,000 c. Filter Reject Line Extension $100,000 d. Upsize Filter Reject Wet Well and Pump System $500,000 e. Pre-Settling Basin $1,000,000 f. Screen Replacement for Mechanical Screens $500,000 g. Flow Study $40,000 h. Preliminary Biosolids Profile $12,000 i. Wastewater Treatment Plant Generator $400,000 Total WWTP Improvements $400,000 $0 $190,000 $800,000 $1,300,000 $312,000 $800,000 General Sewer Improvements Cost of Service Study $250,000 Sanitary Comp. Plan/Model $300,000 $300,000 Sewer Rate Study $50,000 Total General Sewer Improvements $300,000 $0 $50,000 $0 $0 $250,000 $300,000 Total Sanitary Sewer 6 Year CIP Costs $930,000 $1,230,000 $795,000 $2,130,000 $2,040,000 $2,407,000 $1,605,000 (1) The 6-year CIP covers the period of 2012 - 2017. 2011 CIP projects are included for reference. 11-10 City of Marysville November 2011 Sewer Comprehensive Plan PROPOSED SYSTEM IMPROVEMENTS FROM 2018 TO 2031 CIP projects recommended for the 20-year CIP are based both on the results of hydraulic model for 2031 and buildout conditions. Similar to the 6-year CIP, descriptions for each component of the 20-year CIP are included below: SANITARY SEWER MAINS SEWER MAIN OVERSIZING The City has budgeted an annual amount for oversizing sewer mains. An annual amount is shown through 2031. Estimated Project Cost: .......................................................................... $30,000 annually RENEWALS AND REPLACEMENTS An annual amount is shown through 2031 for renewals, replacement of side sewers, and replacement of 8-inch sewer pipe within the sewer system. Estimated Project Cost: ........................................................................ $500,000 annually LAKEWOOD SEWER EXTENSION PROJECT – PHASE 2 (2018) This project is a continuation of the Lakewood Sewer Extension project from the previous Plan. The remaining Phase 2 improvements include construction of a new 36- inch pipeline along 136th St NE from Smokey Point Blvd to connect to Trunk A at 51st Ave NE. This alignment consists of a total of 6,010 linear feet of 36-inch gravity sewer pipe, including the replacement of 1,350 linear feet of existing 30-inch (Trunk A) with 36-inch from 136th St NE to 132nd St NE. Estimated Project Cost: .....................................................................................$6,570,000 88TH STREET NE AT ALLEN CREEK (2022) Due to surcharging and video inspection that revealed sagging in the pipe, 1,020 linear feet of 15-inch gravity sewer will replace existing 12-inch sewer. City staff recognizes that this area is prone to sags in the pipe. This project would be constructed in conjunction with any future road related projects. Estimated Project Cost: .......................................................................................$ 640,000 City of Marysville 11-11 Sewer Comprehensive Plan November 2011 SUNNYSIDE BLVD UPSIZING – 53RD AVE NE to 60TH DR NE (2024) The hydraulic model demonstrated surcharging within the existing 24-inch sewer between 52nd Ave NE and 60th Dr NE. This project includes 3,150 linear feet of 30-inch gravity sewer to replace the existing 24-inch sewer. Estimated Project Cost: .....................................................................................$3,590,000 169TH PL NE AND 27TH PL NE (2026) Significant surcharging occurred in the hydraulic model during 2031 along 169th Pl. NE extending up north along 27th Ave and Spring Lane Ave. The recommended project in this area would be to replace the current 10-inch and 12-inch pipes with 15” pipes for approximately 3,035 lineal feet. This is a lower priority project as future development could be directed south toward an existing 15-inch stub located on 164th Pl. NE or south towards 156th St NE which would thereby allow additional capacity to the north. Estimated Project Cost: .....................................................................................$1,290,000 152ND TRUNK - 51ST TO EAST (2028) This project begins at 51st Street (Trunk A) and extends along 152nd Street to 850-feet east of the railroad tracks (within City limits). The project includes construction of 2,625 linear feet of 21-inch gravity sewer. Estimated Project Cost: .....................................................................................$2,300,000 PUMP STATIONS The primary pump station improvements for the 20-year CIP are upsizing the pumps, wiring, and components at the 51st Street and Soper Hill pump stations. 51ST STREET PUMP STATION UPSIZING (2025) This pump station will be reaching its capacity prior to 2031, so upsizing of the pumps, wiring, controls and telemetry will need to be completed. Estimated Project Cost:………………………………………………………..$250,000 SOPER HILL PUMP STATION (2030) This pump station will be reaching its capacity by 2031, so upsizing of the pumps, wiring, controls, and telemetry will need to be completed. Estimated Project Cost: ........................................................................................$100,000 11-12 City of Marysville November 2011 Sewer Comprehensive Plan WWTP IMPROVEMENTS The most significant 20-year CIP item is biosolids removal, which may be required twice during the next 20 years. Another important improvement includes additional complete mix aerated cells #7 and #8. Sufficient alum storage will also need to be looked at. PRELIMINARY BIOSOLIDS PROFILE (2016 AND 2023) Prior to each biosolids removal project, a preliminary evaluation is recommended to determine the accumulation of biosolids, by location, depth, and solids content. This evaluation will provide the necessary information for scheduling the next project. Estimated Project Cost: ..........................................................................................$12,000 BIOSOLIDS REMOVAL (2018, AND 2025) Biosolids removal is anticipated at 7-year intervals with each project removing approximately 5,600 dry tons. The total amount for each project is $3.4 million. An annual amount of $300,000 is recommended to buffer the amount for the project year. Estimated Project Cost: .....................................................................................$3,400,000 COMPLETE MIX AERATED CELLS #7 AND #8 (2020) Phase 2 construction provided a total of six complete mix, aerated cells to the lagoon system. The addition of cells #7 and #8 will ensure NPDES permit compliance in the future, particularly for CBOD5. Estimated Project Cost: .....................................................................................$4,000,000 ALUM STORAGE (2026) The current storage volume of 7,500 gallons will need to be increased to 10,000 gallons as WWTP flows increase. Estimated Project Cost: ..........................................................................................$35,000 GENERAL SYSTEM IMPROVEMENTS The proposed general system improvements for the 20-year CIP include periodic updates to the Sewer Comprehensive Plan and Sewer Rate Studies. City of Marysville 11-13 Sewer Comprehensive Plan November 2011 SEWER COMPREHENSIVE PLAN/MODEL (2022 AND 2028) This plan will update the City’s CIP and hydraulic model for the collection system. Estimated Project Cost: ........................................................................................$300,000 SEWER RATE STUDY (2018, 2024, AND 2030) This study will review the City’s CIP and O&M costs and evaluate the sewer rates to meet projected needs. Estimated Project Cost: ..........................................................................................$50,000 TOTAL 20-YEAR CIP Table 11-2 summarizes the CIP projects from 2018 to 2031. The total amount for projects from 2018 to 2031 is $34,269,000. The total amount for the 20-year CIP (from 2012 to 2031) is $44,476,000. City of Marysville 11-14 Sewer Comprehensive Plan November 2011 TABLE 11-2 Capital Improvements Plan 2018 - 2031 2017 2018 2019 2020 2021 2022 2023 2024 2025 2026 2027 2028 2029 2030 2031 Sanitary Sewer Mains Sewer Main Oversizing $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 $30,000 Renewals and Replacement $500,000 $500,000 $500,000 $500,000 $500,000 $500,000 $500,000 $500,000 $500,000 $500,000 $500,000 $500,000 $500,000 $500,000 $500,000 Lakewood Sewer Extension: Phase 2 $6,570,000 88th St NE at Allen Creek $640,000 Sunnyside Blvd Upsizing – 53rd St NE to 60th Dr Ne $3,590,000 169th Pl NE and 27th Pl NE $1,290,000 152nd St NE – 51st to East $2,300,000 Total Sanitary Sewer Mains $530,000 $7,100,000 $530,000 $530,000 $530,000 $1,170,000 $530,000 $4,120,000 $530,000 $1,820,000 $530,000 $2,830,000 $530,000 $530,000 $530,000 Pump Stations 51st Street Pump Station Upsizing $250,000 Soper Hill Pump Station Upsizing $100,000 Total Pump Stations $0 $0 $0 $0 $0 $0 $0 $0 $250,000 $0 $0 $0 $0 $100,000 $0 WWTP Improvements Biosolids Removal $300,000 $2,200,000 $300,000 $300,000 $300,000 $300,000 $300,000 $300,000 $1,600,000 $300,000 $300,000 $300,000 $300,000 $300,000 $300,000 Preliminary Biosolids Profile $12,000 $12,000 Alum Storage $35,000 Lagoon Improvements: Cells #7 and #8 $4,000,000 Total WWTP Improvements $300,000 $2,200,000 $300,000 $4,300,000 $300,000 $300,000 $312,000 $300,000 $1,600,000 $335,000 $300,000 $300,000 $300,000 $312,000 $300,000 General System Improvements Sewer Comp. Plan/Model $300,000 $250,000 $250,000 Sewer Rate Study $50,000 $50,000 $50,000 Subtotal $300,000 $50,000 $0 $0 $0 $250,000 $0 $50,000 $0 $0 $0 $250,000 $0 $50,000 $0 Total Sanitary Sewer $1,130,000 $9,350,000 $830,000 $4,830,000 $830,000 $1,720,000 $842,000 $4,470,000 $2,380,000 $2,155,000 $830,000 $3,380,000 $830,000 $992,000 $830,000 City of Marysville 12-1 Sewer Comprehensive Plan June 2011 CHAPTER 12 FINANCIAL PLAN INTRODUCTION This Chapter reviews the financial status of current wastewater system operations and the rates and charges used to fund the maintenance, replacement, and construction of new facilities as recommended in this Plan. WASTEWATER RATES & CHARGES Table 12-1 summarizes wastewater rates and Table 12-2 lists existing GFCs. Current wastewater rates are billed bi-monthly and include uniform rates for residential, multi- family, and motel/hotel customers and flow based rates ($/1,000 gallons) for commercial/industrial customers. Flow based rates for commercial/industrial customers are based on assigned concentrations of BOD (organic loading) with BOD concentrations (mg/L) ranging from 31-100 mg/L for Class 1 and 501-600 mg/L for Class 6 customers. Commercial/industrial customers are charged a minimum base rate plus the volume charge for their given strength class. In addition to the rates shown in Table 12-1, the City has elected to increase rates for 2 percent per year to offset increases in expenses from price inflation. The rate ordinance specifies automatic 2 percent adjustments unless the City Council elects to defer implementation in a given year based on an updated financial review. 12-2 City of Marysville June 2011 Sewer Comprehensive Plan TABLE 12-1 Wastewater Bi-Monthly Rates Customer Classes City Rate Rural Rate Outside UGA Rates(1) Single-family home $75.02 $112.54 $ 150.05 Multiple-residential $71.34 $107.01 $ 142.68 Hotels/Motels per unit $52.55 $ 78.83 $ 105.10 Class 1 (31 to 100 mg/l) per 1,000 gal $ 1.57 $ 2.36 $ 3.14 Class 2 (101 to 200 mg/l) per 1,000 gal $ 2.16 $ 3.24 $ 4.32 Class 3 (201 to 300 mg/l) per 1,000 gal $ 2.76 $ 4.15 $ 5.54 Class 4 (301 to 400 mg/l) per 1,000 gal $ 3.36 $ 5.04 $ 6.72 Class 5 (401 to 500 mg/l) per 1,000 gal $ 3.96 $ 5.93 $ 7.91 Class 6 (501 to 600 mg/l) per 1,000 gal $ 5.74 $ 8.62 $ 11.49 Overnight Camping Individual connections per unit $52.55 $ 78.83 $ 105.10 Other connections each $71.34 $107.01 $ 142.68 Schools Minimum $75.02 Per 1,00 gallons $ 4.26 Restaurants w/o grease trap surcharge $ 3.60 (1) Source: City of Marysville Ordinance No. 2836, effective January 1, 2011. The wastewater utility also utilizes a capital charge for new customers connecting to the wastewater system know as a general facility charge or connection charge. General facility charges (GFCs) are intended to ensure a new customer pays a pro –rata share of both existing facilities from which they will benefit and a share of the cost of planned facilities. Revenues from GFCs are used to minimize the impact on bi-monthly rates to provide new capital facilities required to serve growth. Table 12-2 lists existing GFCs. The City charges higher GFCs for customers outside of City limits (rural) because of higher permitting, planning, and construction costs for projects constructed in the County. For example, Snohomish County requires the City to install a full overlay (instead of a patch) when installing pipe in County roadways. City of Marysville 12-3 Sewer Comprehensive Plan June 2011 TABLE 12-2 Existing General Facility Charges (1) Customer Type City Rate ($/Unit) Rural Rate ($/Unit) Residential GFC (January 1, 2006) $4,490.00 $4,890.00 (1) Source: City of Marysville Ordinance No. 2345, effective January 1, 2000. The City also charges commercial customers a GFC based on the square footage of the building being provided service. These rates are calculated utilizing the residential GFC listed in Table 12-2. FINANCIAL STATUS OF THE EXISTING SYSTEM The City operates a combined utility fund with some revenues and expenses segregated between water, wastewater, and stormwater and others commingled. As part of this analysis historical water/wastewater/stormwater revenues and expenses were segregated and the following analysis presents only those revenues and expenses identified as wastewater related. Further, the City utilizes a detailed schedule of expenses that have been summarized for presentation purposes. HISTORICAL OPERATING CASH FLOWS Table 12-3 presents a summary of historical revenues and expenses associated with the wastewater system. The data presented in Table 12-3 represents cash flows from operating activities and does not include significant capital improvement costs. Positive operating cash flows indicate the ability of existing revenue sources to fund existing operations and meet current debt obligations. This net operating revenue is then available to fund capital construction, additional debt obligations, or to build capital reserves. 12-4 City of Marysville June 2011 Sewer Comprehensive Plan TABLE 12-3 Historical Wastewater Revenues and Expenses(1) Operating Cash Flows 2008 2009 2010 (+) Total Revenues $ 9,855,328 $ 9,724,904 $ 9,846,333 (-) Total Operations & Maintenance $ (4,393,875) $ (4,466,021) $ (5,028,102) (-) Total Debt(2) $ (3,278,600) $ (3,274,700) $ (4,363,957) Net Operating Revenue $ 2,182,853 $ 1,984,184 $ 454,274 (1) These wastewater cash flows are estimated based on a segregation of combined water, wastewater, and stormwater revenues and expenses assuming commingled accounts are split according to the Utility Rate Model created for the City by Peninsula Financial Consulting. (2) Some debts constructed both water and wastewater facilities and were therefore segregated evenly between water and sewer, other debts constructed water, wastewater, and stormwater facilities and were therefore segregated based on the cost of the infrastructure as a percent of the total debt. Additional debts were identified as constructing only water facilities and are not included. As can be seen in Table 12-3, the total amount expended on debt rose sharply from 2009 to 2010. In an effort to reduce outstanding debt the City opted to call, early, the remaining bonds of an outstanding 1998 refunding issue of a 1993 bond. In doing so the City will save interest costs in future years, increasing net operating revenue. PROJECTED OPERATING CASH FLOWS The City’s projected operating cash flows show a gradual increase in both estimated revenues and operations and maintenance costs. Revenue increases are attributable to the aforementioned 2 percent annual increase and anticipated annual growth. Additional expenditures are due to the effect of price inflation and system growth. A budget forecast summary is presented in Table 12-4. 12-5 City of Marysville June 2011 Sewer Comprehensive Plan TABLE 12-4 Projected Operating Cash Flows Operating Cash Flows 2011 2012 2013 2014 2015 2016 2017 (+) Total Revenues(1) $ 8,768,567 $ 8,768,567 $ 9,389,600 $ 9,533,700 $ 9,770,500 $ 10,078,900 $ 10,358,900 (-) Total Operations & Maintenance $ (5,282,569) $ (5,812,597) $ (5,835,800) $ (6,032,700) $ (6,245,900) $ (6,417,900) $ (6,652,700) (-) Total Debt $ (2,861,700) $ (2,467,100) $ (2,997,500) $ (2,992,200) $ (2,986,300) $ (2,980,000) $ (2,975,700) Net Operating Revenue $ 624,298 $ 488,870 $ 556,300 $ 508,800 $ 538,300 $ 681,000 $ 730,500 (1) Projected revenues include the 2% annual rate increase as mentioned on page 12-1 of this section. City of Marysville 12-6 Sewer Comprehensive Plan June 2011 CAPITAL FUNDS AVAILABLE FOR FUTURE IMPROVEMENTS As indicated in Table 12-4, wastewater operations are expected to generate revenues in excess of O&M and debt costs that will be available for funding future capital projects. The wastewater utility also generates capital revenues from sources such as general facility charges and recovery contracts (latecomer agreements) that also are available for funding capital projects. Table 12-5 presents a summary of forecasted net revenue from operations and capital revenues that are available for funding planned capital improvements. As shown in Table 12-5, the wastewater utility is expected to generate from around $1 million to $1.5 million per year in excess revenues that will be available to construct future facilities identified in this Plan. Table 11-1 presents current (2011) and proposed capital projects for the 6-year CIP (2012 – 2017). The total amount for 2012 – 2017 is $10.2 million. Sanitary sewer main projects account for $4.6 million, while Wastewater Treatment Plant improvements total $3.4 million. The remaining funds are dedicated to pump station upgrades and general system improvements. The City must generate $10.2 million over the next six years in order to fund planned capital improvements. According to the projected cash flows summarized in Table 12-5, the wastewater utility will generate approximately $7.3 million between 2012 and 2017. Due to rate increases in previous years the wastewater utility can fund most of its planned capital improvements from projected operating and capital revenues. However, the planned improvements exceed the expected revenue by $2.9 million over the next 6- years. Several alternative funding options, grants or low interest rate loans such as Public Works Trust Fund Loans, are available to the City for consideration in funding capital projects for the wastewater utility. These sources shall be considered when determining additional funding sources for the capital improvement projects in the 6-year CIP. 12-7 City of Marysville June 2011 Sewer Comprehensive Plan TABLE 12-5 Projected Funds Available for Capital Funding Cash Flows 2011 2012 2013 2014 2015 2016 2017 Transfer from Operations $ 624,298 $ 488,870 $ 556,300 $ 508,800 $ 538,300 $681,000 $ 735,500 City Sewer Recovery Contracts $ 50,000 $ 30,000 $ 60,000 $ 66,000 $ 66,000 $ 102,000 $ 102,000 Sewer Connection Charges $ 400,000 $ 400,000 $ 449,000 $ 493,900 $ 493,900 $ 763,300 $ 763,300 Total Cash Flows $ 1,074,298 $ 918,870 $ 1,065,300 $ 1,062,700 $ 1,092,200 $ 1,546,300 $ 1,600,800 (1) Transfers from operations are net revenues listed in Table 12-4. (3) City wastewater recovery contracts are estimated payments from new connections for local facilities funded by the City for a specific service area to be repaid by as new customers in the latecomer’s area connect to the system. The amounts shown are estimates based on the Utility Rate Model created for the City by Peninsula Financial Consulting. APPENDIX A NPDES PERMIT NO. WA-002249-7 Page 1 of 35 Permit No. WA-002249-7 Issuance Date: July 1, 2005 Effective Date: July 1, 2005 Expiration Date: June 30, 2010 NATIONAL POLLUTANT DISCHARGE ELIMINATION SYSTEM WASTE DISCHARGE PERMIT No. WA-002249-7 State of Washington DEPARTMENT OF ECOLOGY Northwest Regional Office 3190 – 160th Avenue SE Bellevue, WA 98008-5452 In compliance with the provisions of The State of Washington Water Pollution Control Law Chapter 90.48 Revised Code of Washington and The Federal Water Pollution Control Act (The Clean Water Act) Title 33 United States Code, Section 1251 et seq. CITY OF MARYSVILLE 80 Columbia Avenue Marysville, WA 98270 Plant Location: Columbia Avenue and Ebey Slough Receiving Water: Steamboat Slough (Snohomish River) Port Gardner Bay Water Body I.D. No.: WA-07-1005 WA-PS-0030 Discharge Location: Steamboat Slough (Outfall 001) Latitude: 48° 02' 08" N Longitude: 122° 10' 20" W Port Gardner Bay (Outfall 100) Latitude: 47° 58' 10" N Longitude: 122° 14' 48" W Plant Type: Aerated and Oxidation (Waste Stabilization) Pond System is authorized to discharge in accordance with the special and general conditions that follow. Kevin C. Fitzpatrick Water Quality Section Manager Northwest Regional Office Washington State Department of Ecology Page 2 of 35 Permit No. WA-002249-7 TABLE OF CONTENTS SUMMARY OF PERMIT REPORT SUBMITTALS.....................................................................4 SPECIAL CONDITIONS S1. DISCHARGE LIMITATIONS............................................................................................5 A. Effluent Limitations – Low River Flow Period (July through October) B. Effluent Limitations – High River Flow Period (November through June) C. Mixing Zone Descriptions S2. MONITORING REQUIREMENTS....................................................................................8 A. Monitoring Schedule B. Sampling and Analytical Procedures C. Flow Measurement D. Laboratory Accreditation S3. REPORTING AND RECORDKEEPING REQUIREMENTS.........................................10 A. Reporting B. Records Retention C. Recording of Results D. Additional Monitoring by the Permittee E. Noncompliance Notification F. Maintaining a Copy of This Permit G. Reporting - Shellfish Protection S4. FACILITY LOADING......................................................................................................12 A. Design Criteria B. Plans for Maintaining Adequate Capacity C. Duty to Mitigate D. Notification of New or Altered Sources E. Infiltration and Inflow Evaluation F. Wasteload Assessment S5. OPERATION AND MAINTENANCE.............................................................................14 A. Certified Operator B. O & M Program C. Short-term Reduction D. Electrical Power Failure E. Prevent Connection of Inflow F. Bypass Procedures G. Operations and Maintenance Manual S6. PRETREATMENT............................................................................................................17 A. General Requirements B. Wastewater Discharge Permit Required C. Identification and Reporting of Existing, New, and Proposed Industrial Users D. Industrial User Survey E. Duty to Enforce Discharge Prohibitions Page 3 of 35 Permit No. WA-002249-7 S7. RESIDUAL SOLIDS.........................................................................................................20 S8. ACUTE TOXICITY..........................................................................................................20 A. Effluent Limit for Acute Toxicity (Steamboat Slough discharge only) B. Monitoring for Compliance With an Effluent Limit for Acute Toxicity C. Response to Noncompliance With an Effluent Limit for Acute Toxicity D. Sampling and Reporting Requirements S9. CHRONIC TOXICITY......................................................................................................23 A. Effluent Characterization B. Effluent Limit for Chronic Toxicity (Steamboat Slough discharge only) C. Monitoring for Compliance with an Effluent Limit for Chronic Toxicity D. Response to Noncompliance With an Effluent Limit for Chronic Toxicity E. Monitoring When There Is No Permit Limit for Chronic Toxicity F. Sampling and Reporting Requirements S10. ADDITIONAL CHEMICAL ANALYSIS OF INFLUENT AND EFFLUENT...............27 A. Additional Effluent Testing B. Priority Pollutant Scans C. Protocols D. Quality Assurance/Quality Control Procedures S11. OUTFALL EVALUATION..............................................................................................28 GENERAL CONDITIONS G1. SIGNATORY REQUIREMENTS.....................................................................................29 G2. RIGHT OF INSPECTION AND ENTRY.........................................................................30 G3. PERMIT ACTIONS...........................................................................................................30 G4. REPORTING PLANNED CHANGES..............................................................................31 G5. PLAN REVIEW REQUIRED...........................................................................................32 G6. COMPLIANCE WITH OTHER LAWS AND STATUTES.............................................32 G7. DUTY TO REAPPLY.......................................................................................................32 G8. TRANSFER OF THIS PERMIT .......................................................................................32 G9. REDUCED PRODUCTION FOR COMPLIANCE..........................................................33 G10. REMOVED SUBSTANCES.............................................................................................33 G11. DUTY TO PROVIDE INFORMATION...........................................................................33 G12. OTHER REQUIREMENTS OF 40 CFR...........................................................................33 G13. ADDITIONAL MONITORING........................................................................................33 G14. PAYMENT OF FEES........................................................................................................33 G15. PENALTIES FOR VIOLATING PERMIT CONDITIONS .............................................33 G16. UPSET...............................................................................................................................34 G17. PROPERTY RIGHTS........................................................................................................34 G18. DUTY TO COMPLY ........................................................................................................34 G19. TOXIC POLLUTANTS.....................................................................................................34 G20. PENALTIES FOR TAMPERING.....................................................................................34 G21. REPORTING ANTICIPATED NONCOMPLIANCE......................................................35 G22. REPORTING OTHER INFORMATION..........................................................................35 G23. COMPLIANCE SCHEDULES .........................................................................................35 Page 4 of 35 Permit No. WA-002249-7 SUMMARY OF PERMIT REPORT SUBMITTALS Refer to the Special and General Conditions of this permit for additional submittal requirements. Permit Section Submittal Frequency First Submittal Date S3. Discharge Monitoring Report Monthly August 15, 2005 S3.E. Noncompliance Notification As necessary S3.G. Shellfish Protection As necessary S4.B. Plans for Maintaining Adequate Capacity As necessary S4.D. Notification of New or Altered Sources As necessary S4.E. Infiltration and Inflow Evaluation 2/permit cycle June 1, 2006 June 1, 2009 S4.F. Wasteload Assessment 1/permit cycle June 1, 2009 S5.G. Operations and Maintenance Manual 1/permit cycle October 1, 2005 S5.G. Operations and Maintenance Manual Update or Review Confirmation Letter Annually or as necessary S6.D.1. Industrial User Survey 1/permit cycle June 1, 2006 S6.D.2. Industrial User Survey Update Annually June 1, 2007 S8.B. Acute Toxicity Compliance Monitoring Reports 3/year December 15, 2005 S8.C. Acute Toxicity: “Causes and Preventative Measures for Transient Events Report” As necessary S8.C. Acute Toxicity TI/RE Plan As necessary S9.A. Chronic Toxicity Characterization Data 2/permit cycle (conduct testing in November 2005 and May 2006) December 15, 2005 June 15, 2006 S9.C. Chronic Toxicity Compliance Monitoring Reports Biannually, if needed S9.D. Chronic Toxicity: “Causes and Preventative Measures for Transient Events Report” As necessary S9.D. Chronic Toxicity TI/RE Plan As necessary S9.E. Chronic Toxicity Effluent Characterization with Permit Renewal Application 2/permit cycle (conduct testing in May 2009 and November 2009) June 30, 2009 S10.A. Chemical Analysis of Influent and Effluent Annually December 15, 2005 S11. Outfall Evaluation 1/permit cycle June 30, 2009 G1. Notice of Change in Authorization As necessary G4. Reporting Planned Changes As necessary G5. Engineering Report for Construction or Modification Activities As necessary G7. Application for Permit Renewal 1/permit cycle December 30, 2009 G21. Reporting Anticipated Noncompliance As necessary G22. Reporting Other Information As necessary Page 5 of 35 Permit No. WA-002249-7 SPECIAL CONDITIONS S1. DISCHARGE LIMITATIONS A. Effluent Limitations – Low River Flow Period (July through October) All discharges and activities authorized by this permit shall be consistent with the terms and conditions of this permit. The discharge of any of the following pollutants more frequently than, or at a level in excess of, that identified and authorized by this permit shall constitute a violation of the terms and conditions of this permit. Beginning on the effective date of this permit and lasting through the expiration date, the Permittee is authorized to discharge municipal wastewater at the permitted location subject to complying with the following limitations: EFFLUENT LIMITATIONSa: Steamboat Slough - OUTFALL #001 Outfall #001 may be used only to discharge treated effluent for the purpose of outfall and diffuser flushing and maintenance. Maximum frequency of this use shall be once weekly for up to three hours at a flow rate of up to 8 MGD. Parameter Average Monthly Average Weekly Carbonaceous Biochemical Oxygen Demandb (5-day) 25 mg/L 40 mg/L Total Suspended Solidsc 30 mg/L 45 mg/L Fecal Coliform Bacteria 200/100 mL 400/100 mL pHd Daily minimum is equal to or greater than 6 and the daily maximum is less than or equal to 9. Parameter Average Monthly Maximum Dailye Carbonaceous Biochemical Oxygen Demand (5-day) 419 lbs/day 672 lbs/day Total Ammonia (as N) 178 lbs/day 403 lbs/day EFFLUENT LIMITATIONSa: Port Gardner - OUTFALL #100 Parameter Average Monthly Average Weekly Carbonaceous Biochemical Oxygen Demandb (5-day) 25 mg/L 2,650 lbs/day 40 mg/L 4,240 lbs/day Total Suspended Solidsc 30 mg/L 3,180 lbs/day 45 mg/L 4,770 lbs/day Fecal Coliform Bacteria 200/100 mL 400/100 mL pHd Daily minimum is equal to or greater than 6 and the daily maximum is less than or equal to 9. a The average monthly and weekly effluent limitations are based on the arithmetic mean of the samples taken with the exception of fecal coliform, which is based on the geometric mean. b The average monthly effluent concentration for CBOD5 shall not exceed 25 mg/L or 15 percent of the monthly average influent concentration, whichever is more stringent. Page 6 of 35 Permit No. WA-002249-7 c The average monthly effluent concentration for Total Suspended Solids shall not exceed 30 mg/L or 15 percent of the monthly average influent concentration, whichever is more stringent. d Indicates the range of permitted values. Effluent values for pH collected as single grab samples shall not exceed the limits of 6.0-9.0 where such values are attributable to inorganic industrial contributions. e The maximum daily effluent limitation is defined as the highest allowable daily discharge. The daily discharge means the discharge of a pollutant measured during a calendar day. For pollutants with limitations expressed in units of mass, the daily discharge is calculated as the total mass of the pollutant discharged over the day. For other units of measurement, the daily discharge is the average measurement of the pollutant over the day. B. Effluent Limitations – High River Flow Period (November through June) All discharges and activities authorized by this permit shall be consistent with the terms and conditions of this permit. The discharge of any of the following pollutants more frequently than, or at a level in excess of, that identified and authorized by this permit shall constitute a violation of the terms and conditions of this permit. Beginning on the effective date of this permit and lasting through the expiration date, the Permittee is authorized to discharge municipal wastewater at the permitted location subject to complying with the following limitations: EFFLUENT LIMITATIONSa: Steamboat Slough - OUTFALL #001 Parameter Average Monthly Average Weekly Flow 6.6 MGD Carbonaceous Biochemical Oxygen Demandb (5-day) 25 mg/L 40 mg/L Total Suspended Solidsc 30 mg/L 45 mg/L Fecal Coliform Bacteria 200/100 mL 400/100 mL pHd Daily minimum is equal to or greater than 6 and the daily maximum is less than or equal to 9. Parameter Acute Toxicity The effluent limit for acute toxicity is no acute toxicity detected in a test concentration representing the acute critical effluent concentration (ACEC). See Section S8. Chronic Toxicity An effluent limit for chronic toxicity may apply after characterization testing is complete. See Section S9. Page 7 of 35 Permit No. WA-002249-7 EFFLUENT LIMITATIONSa: Port Gardner - OUTFALL #100 Parameter Average Monthly Average Weekly Carbonaceous Biochemical Oxygen Demandb (5-day) 25 mg/L 40 mg/L Total Suspended Solidsc 30 mg/L 45 mg/L Fecal Coliform Bacteria 200/100 mL 400/100 mL pHd Daily minimum is equal to or greater than 6 and the daily maximum is less than or equal to 9. EFFLUENT LIMITATIONSa: COMBINED OUTFALLS #001 + 100 Parameter Average Monthly Average Weekly Carbonaceous Biochemical Oxygen Demand (5-day) 2,650 lbs/day 4,240 lbs/day Total Suspended Solids 3,180 lbs/day 4,770 lbs/day a The average monthly and weekly effluent limitations are based on the arithmetic mean of the samples taken with the exception of fecal coliform, which is based on the geometric mean. b The average monthly effluent concentration for CBOD5 shall not exceed 25 mg/L or 15 percent of the monthly average influent concentration, whichever is more stringent. c The average monthly effluent concentration for Total Suspended Solids shall not exceed 30 mg/L or 15 percent of the monthly average influent concentration, whichever is more stringent. d Indicates the range of permitted values. Effluent values for pH collected as single grab samples shall not exceed the limits of 6.0-9.0 where such values are attributable to inorganic industrial contributions. C. Mixing Zone Descriptions The maximum boundaries of the mixing zones are defined as follows: Steamboat Slough - Outfall 001: 1. The width of the mixing zone is limited to 98 feet and is centered on the middle of the multi-port diffuser 180 feet from the east bank of the river at MLLW. 2. The length of the mixing zone downstream perpendicular to the outfall is 214 feet; the length of the mixing zone upstream perpendicular to the outfall is 214 feet. The Chronic Dilution Factor DFc = 27.1. Page 8 of 35 Permit No. WA-002249-7 3. The zone where acute criteria may be exceeded shall extend a distance of 21.5 feet in any horizontal direction from the diffuser and extends vertically to the surface. The Acute Dilution Factor DFa = 10.9. Port Gardner – Outfall 100: 1. The mixing zone shall not extend in any horizontal direction from the discharge ports for a distance greater than two hundred feet plus the depth of water over the discharge ports as measured during mean lower low water. 2. A zone where acute criteria may be exceeded shall not extend beyond ten percent of the distance to the boundary of the mixing zone as measured independently from the discharge ports. 3. The Chronic Dilution Factor DFc = 696. The Acute Dilution Factor DFa = 156. S2. MONITORING REQUIREMENTS A. Monitoring Schedule The Permittee shall monitor in accordance with the following schedule: Category Parameter Units Sample Point Minimum Sampling Frequency Sample Type Wastewater Influent Flow MGD Plant influent Continuous Measurement “ CBOD5 mg/l Plant influent 3/week 24-hr composite “ BOD5 mg/l Plant influent 2/month 24-hr composite “ TSS mg/l Plant influent 3/week 24-hr composite Wastewater Effluent Flow to Steamboat Slough MGD Effluent to Steamboat Slough Continuous Measurement “ Flow to Everett WWTP MGD Effluent to Everett Continuous Measurement “ CBOD5 mg/l Final Effluent 3/week 24-hr composite “ TSS mg/l Final Effluent 3/week 24-hr composite “ Fecal Coliform Bacteria Cfu/100 mL Final Effluent 3/week Grab “ pH Standard Units Final Effluent 5/week Grab “ Total ammonia mg/l Final Effluent 2/month 24-hr composite Page 9 of 35 Permit No. WA-002249-7 Category Parameter Units Sample Point Minimum Sampling Frequency Sample Type “ Pollutants listed in EPA form 3510-2A parts B.6 and D for NPDES permit reapplication (See Section S10.) Final Effluent 1/year 24-hr composite Acute Toxicity Testing See Section S8. Final Effluent 3/year (February, May, and November) 24-hr composite Chronic Toxicity Testing See Section S9. Final Effluent 2/year (May and November) in first and last year 24-hr composite B. Sampling and Analytical Procedures Samples and measurements taken to meet the requirements of this permit shall be representative of the volume and nature of the monitored parameters, including representative sampling of any unusual discharge or discharge condition, including bypasses, upsets, and maintenance-related conditions affecting effluent quality. Sampling and analytical methods used to meet the monitoring requirements specified in this permit shall conform to the latest revision of the Guidelines Establishing Test Procedures for the Analysis of Pollutants contained in 40 CFR Part 136 or to the latest revision of Standard Methods for the Examination of Water and Wastewater (APHA), unless otherwise specified in this permit or approved in writing by the Department of Ecology (Department). C. Flow Measurement Appropriate flow measurement devices and methods consistent with accepted scientific practices shall be selected and used to ensure the accuracy and reliability of measurements of the quantity of monitored flows. The devices shall be installed, calibrated, and maintained to ensure that the accuracy of the measurements is consistent with the accepted industry standard for that type of device. Frequency of calibration shall be in conformance with manufacturer's recommendations and at a minimum frequency of at least one calibration per year. Calibration records shall be maintained for at least three years. Page 10 of 35 Permit No. WA-002249-7 D. Laboratory Accreditation All monitoring data required by the Department shall be prepared by a laboratory registered or accredited under the provisions of, Accreditation of Environmental Laboratories, Chapter 173-50 WAC. Flow, temperature, settleable solids, conductivity, pH, and internal process control parameters are exempt from this requirement. Conductivity and pH shall be accredited if the laboratory must otherwise be registered or accredited. The Department exempts crops, soils, and hazardous waste data from this requirement pending accreditation of laboratories for analysis of these media. S3. REPORTING AND RECORDKEEPING REQUIREMENTS The Permittee shall monitor and report in accordance with the following conditions. The falsification of information submitted to the Department shall constitute a violation of the terms and conditions of this permit. A. Reporting The first monitoring period begins on the effective date of the permit. Monitoring results shall be submitted monthly. Monitoring data obtained during each monitoring period shall be summarized, reported, and submitted on a Discharge Monitoring Report (DMR) form provided, or otherwise approved, by the Department. DMR forms shall be received by the Department no later than the 15th day of the month following the completed monitoring period, unless otherwise specified in this permit. Priority pollutant analysis data shall be submitted no later than forty-five (45) days following the monitoring period. Unless otherwise specified, all toxicity test data shall be submitted within sixty (60) days after the sample date. The report(s) shall be sent to the Department of Ecology, Northwest Regional Office, 3190 – 160th Avenue SE, Bellevue, Washington 98008-5452. All laboratory reports providing data for organic and metal parameters shall include the following information: sampling date, sample location, date of analysis, parameter name, CAS number, analytical method/number, method detection limit (MDL), laboratory practical quantitation limit (PQL), reporting units, and concentration detected. Discharge Monitoring Report forms must be submitted monthly whether or not the facility was discharging. If there was no discharge during a given monitoring period, submit the form as required with the words "no discharge" entered in place of the monitoring results. B. Records Retention The Permittee shall retain records of all monitoring information for a minimum of three (3) years. Such information shall include all calibration and maintenance records and all original recordings for continuous monitoring instrumentation, copies of all reports required by this permit, and records of all data used to complete the application for this Page 11 of 35 Permit No. WA-002249-7 permit. This period of retention shall be extended during the course of any unresolved litigation regarding the discharge of pollutants by the Permittee or when requested by the Department. C. Recording of Results For each measurement or sample taken, the Permittee shall record the following information: (1) the date, exact place, method, and time of sampling or measurement; (2) the individual who performed the sampling or measurement; (3) the dates the analyses were performed; (4) the individual who performed the analyses; (5) the analytical techniques or methods used; and (6) the results of all analyses. D. Additional Monitoring by the Permittee If the Permittee monitors any pollutant more frequently than required by this permit using test procedures specified by Condition S2 of this permit, then the results of such monitoring shall be included in the calculation and reporting of the data submitted in the Permittee's DMR. E. Noncompliance Notification In the event the Permittee is unable to comply with any of the terms and conditions of this permit due to any cause, the Permittee shall: 1. Immediately take action to stop, contain, and cleanup unauthorized discharges or otherwise stop the noncompliance, correct the problem and, if applicable, repeat sampling and analysis of any noncompliance immediately and submit the results to the Department within thirty (30) days after becoming aware of the violation. 2. Immediately notify the Department of the failure to comply. 3. Submit a detailed, written report to the Department within thirty (30) days (five [5] days for upsets and bypasses), unless requested earlier by the Department. The report shall contain a description of the noncompliance, including exact dates and times, and if the noncompliance has not been corrected, the anticipated time it is expected to continue; and steps taken or planned to reduce, eliminate, and prevent reoccurrence of the noncompliance. Compliance with these requirements does not relieve the Permittee from responsibility to maintain continuous compliance with the terms and conditions of this permit or the resulting liability for failure to comply. F. Maintaining a Copy of This Permit A copy of this permit must be kept at the treatment plant and be made available upon request to the public or Ecology inspectors. Page 12 of 35 Permit No. WA-002249-7 G. Reporting - Shellfish Protection Unauthorized discharges, such as collection system overflows, plant bypasses, or failure of the disinfection system, shall be reported immediately to the Department of Ecology and the Department of Health, Shellfish Program. The Department of Ecology's Northwest Regional Office 24-hr. number is 425-649-7000, and the Department of Health's Shellfish 24-hr. number is 360-236-3330. S4. FACILITY LOADING A. Design Criteria Flows or waste loadings of the following design criteria for the permitted treatment facility shall not be exceeded: Average flow for the maximum month: 12.7 MGD BOD5 loading for the maximum month: 20,143 lbs/day TSS loading for the maximum month: 24,229 lbs/day B. Plans for Maintaining Adequate Capacity The Permittee shall submit to the Department a plan and a schedule for continuing to maintain capacity when: 1. The actual flow or waste load reaches 85 percent of any one of the design criteria in S4.A for three consecutive months; or 2. When the projected increase would reach design capacity within five years, whichever occurs first. If such a plan is required, it shall contain a plan and schedule for continuing to maintain capacity. The capacity as outlined in this plan must be sufficient to achieve the effluent limitations and other conditions of this permit. This plan shall address any of the following actions or any others necessary to meet the objective of maintaining capacity. 1. Analysis of the present design including the introduction of any process modifications that would establish the ability of the existing facility to achieve the effluent limits and other requirements of this permit at specific levels in excess of the existing design criteria specified in paragraph A, above. 2. Reduction or elimination of excessive infiltration and inflow of uncontaminated ground and surface water into the sewer system. 3. Limitation on future sewer extensions or connections or additional waste loads. Page 13 of 35 Permit No. WA-002249-7 4. Modification or expansion of facilities necessary to accommodate increased flow or waste load. 5. Reduction of industrial or commercial flows or waste loads to allow for increasing sanitary flow or waste load. Engineering documents associated with the plan must meet the requirements of WAC 173-240-060, "Engineering Report," and be approved by the Department prior to any construction. The plan shall specify any contracts, ordinances, methods for financing, or other arrangements necessary to achieve this objective. C. Duty to Mitigate The Permittee is required to take all reasonable steps to minimize or prevent any discharge or sludge use or disposal in violation of this permit that has a reasonable likelihood of adversely affecting human health or the environment. D. Notification of New or Altered Sources The Permittee shall submit written notice to the Department whenever any new discharge or a substantial change in volume or character of an existing discharge into the POTW is proposed which: (1) would interfere with the operation of, or exceed the design capacity of, any portion of the POTW; (2) is not part of an approved general sewer plan or approved plans and specifications; or (3) would be subject to pretreatment standards under 40 CFR Part 403 and Section 307(b) of the Clean Water Act. This notice shall include an evaluation of the POTW's ability to adequately transport and treat the added flow and/or waste load, the quality and volume of effluent to be discharged to the POTW, and the anticipated impact on the Permittee’s effluent [40 CFR 122.42(b)]. E. Infiltration and Inflow Evaluation 1. The Permittee shall conduct an infiltration and inflow evaluation twice during the permit term. Refer to the U.S. EPA publication, I/I Analysis and Project Certification, available as Publication No. 97-03 at: Publications Office, Department of Ecology, PO Box 47600, Olympia, WA 98504-7600. Plant monitoring records may be used to assess measurable infiltration and inflow. 2. A report shall be prepared which summarizes any measurable infiltration and inflow. If infiltration and inflow have increased by more than 15 percent from that found in the first report based on equivalent rainfall, the report shall contain a plan and a schedule for: (1) locating the sources of infiltration and inflow; and (2) correcting the problem. 3. The reports shall be submitted by June 1, 2006, and June 1, 2009. Page 14 of 35 Permit No. WA-002249-7 F. Wasteload Assessment The Permittee shall conduct an assessment of their flow and waste load and submit a report to the Department by June 1, 2009. The report shall contain the following: an indication of compliance or noncompliance with the permit effluent limitations; a comparison between the existing and design monthly average dry weather and wet weather flows, peak flows, BOD, and total suspended solids loadings. The report shall also state the present and design population or population equivalent, projected population growth rate, and the estimated date upon which the design capacity is projected to be reached, according to the most restrictive of the parameters above. S5. OPERATION AND MAINTENANCE The Permittee shall at all times properly operate and maintain all facilities and systems of treatment and control (and related appurtenances) which are installed to achieve compliance with the terms and conditions of this permit. Proper operation and maintenance also includes adequate laboratory controls and appropriate quality assurance procedures. This provision requires the operation of back-up or auxiliary facilities or similar systems, which are installed by a Permittee only when the operation is necessary to achieve compliance with the conditions of this permit. A. Certified Operator An operator certified for at least a Class III plant by the state of Washington shall be in responsible charge of the day-to-day operation of the wastewater treatment plant. An operator certified for at least a Class II plant shall be in charge during all regularly scheduled shifts. B. O & M Program The Permittee shall institute an adequate operation and maintenance program for the entire sewage system. Maintenance records shall be maintained on all major electrical and mechanical components of the treatment plant, as well as the sewage system and pumping stations. Such records shall clearly specify the frequency and type of maintenance recommended by the manufacturer and shall show the frequency and type of maintenance performed. These maintenance records shall be available for inspection at all times. C. Short-term Reduction If a Permittee contemplates a reduction in the level of treatment that would cause a violation of permit discharge limitations on a short-term basis for any reason, and such reduction cannot be avoided, the Permittee shall give written notification to the Department, if possible, thirty (30) days prior to such activities, detailing the reasons for, length of time of, and the potential effects of the reduced level of treatment. This notification does not relieve the Permittee of its obligations under this permit. Page 15 of 35 Permit No. WA-002249-7 D. Electrical Power Failure The Permittee is responsible for maintaining adequate safeguards to prevent the discharge of untreated wastes or wastes not treated in accordance with the requirements of this permit during electrical power failure at the treatment plant and/or sewage lift stations either by means of alternate power sources, standby generator, or retention of inadequately treated wastes. The Permittee shall maintain Reliability Class II (EPA 430-99-74-001) at the wastewater treatment plant, which requires a backup power source sufficient to operate all vital components and critical lighting and ventilation during peak wastewater flow conditions, except vital components used to support the secondary processes (i.e., mechanical aerators or aeration basin air compressors) need not be operable to full levels of treatment, but shall be sufficient to maintain the biota. E. Prevent Connection of Inflow The Permittee shall strictly enforce their sewer ordinances and not allow the connection of inflow (roof drains, foundation drains, etc.) to the sanitary sewer system. F. Bypass Procedures Bypass, which is the intentional diversion of waste streams from any portion of a treatment facility, is prohibited, and the Department may take enforcement action against a Permittee for bypass unless one of the following circumstances (1, 2, or 3) is applicable. 1. Bypass for essential maintenance without the potential to cause violation of permit limits or conditions. Bypass is authorized if it is for essential maintenance and does not have the potential to cause violations of limitations or other conditions of this permit, or adversely impact public health as determined by the Department prior to the bypass. The Permittee shall submit prior notice, if possible, at least ten (10) days before the date of the bypass. 2. Bypass which is unavoidable, unanticipated, and results in noncompliance of this permit. This bypass is permitted only if: a. Bypass is unavoidable to prevent loss of life, personal injury, or severe property damage. “Severe property damage” means substantial physical damage to property, damage to the treatment facilities which would cause them to become inoperable, or substantial and permanent loss of natural resources which can reasonably be expected to occur in the absence of a bypass. Page 16 of 35 Permit No. WA-002249-7 b. There are no feasible alternatives to the bypass, such as the use of auxiliary treatment facilities, retention of untreated wastes, stopping production, maintenance during normal periods of equipment downtime (but not if adequate backup equipment should have been installed in the exercise of reasonable engineering judgement to prevent a bypass which occurred during normal periods of equipment downtime or preventative maintenance), or transport of untreated wastes to another treatment facility. c. The Department is properly notified of the bypass as required in Condition S3E of this permit. 3. Bypass which is anticipated and has the potential to result in noncompliance of this permit The Permittee shall notify the Department at least thirty (30) days before the planned date of bypass. The notice shall contain: (1) a description of the bypass and its cause; (2) an analysis of all known alternatives which would eliminate, reduce, or mitigate the need for bypassing; (3) a cost-effectiveness analysis of alternatives including comparative resource damage assessment; (4) the minimum and maximum duration of bypass under each alternative; (5) a recommendation as to the preferred alternative for conducting the bypass; (6) the projected date of bypass initiation; (7) a statement of compliance with SEPA; (8) a request for modification of water quality standards as provided for in WAC 173-201A-110, if an exceedance of any water quality standard is anticipated; and (9) steps taken or planned to reduce, eliminate, and prevent reoccurrence of the bypass. For probable construction bypasses, the need to bypass is to be identified as early in the planning process as possible. The analysis required above shall be considered during preparation of the engineering report or facilities plan and plans and specifications and shall be included to the extent practical. In cases where the probable need to bypass is determined early, continued analysis is necessary up to and including the construction period in an effort to minimize or eliminate the bypass. The Department will consider the following prior to issuing an administrative order for this type of bypass: a. If the bypass is necessary to perform construction or maintenance-related activities essential to meet the requirements of this permit. b. If there are feasible alternatives to bypass, such as the use of auxiliary treatment facilities, retention of untreated wastes, stopping production, maintenance during normal periods of equipment down time, or transport of untreated wastes to another treatment facility. c. If the bypass is planned and scheduled to minimize adverse effects on the public and the environment. Page 17 of 35 Permit No. WA-002249-7 After consideration of the above and the adverse effects of the proposed bypass and any other relevant factors, the Department will approve or deny the request. The public shall be notified and given an opportunity to comment on bypass incidents of significant duration, to the extent feasible. Approval of a request to bypass will be by administrative order issued by the Department under RCW 90.48.120. G. Operations and Maintenance Manual The approved Operations and Maintenance Manual shall be kept available at the treatment plant and all operators shall follow the instructions and procedures of this manual. An updated Operations and Maintenance (O&M) Manual shall be prepared by the Permittee in accordance with WAC 173-240-080 and be submitted to the Department for approval by October 1, 2005. In addition to requirements of WAC 173-240-080 (1) through (5) the O&M Manual shall include: 1. Emergency procedures for plant shutdown and cleanup in event of wastewater system upset or failure. 2. Wastewater system maintenance procedures that contribute to the generation of process wastewater. 3. Any directions to maintenance staff when cleaning, or maintaining other equipment or performing other tasks which are necessary to protect the operation of the wastewater system (e.g. defining maximum allowable discharge rate for draining a tank, blocking all floor drains before beginning the overhaul of a stationary engine). 4. The treatment plant process control monitoring schedule. 5. Operation instructions for the Effluent Pump Station and use of the Steamboat Slough outfall. The O&M Manual shall be reviewed by the Permittee at least annually and the Permittee shall confirm this review by letter to the Department. Substantial changes or updates to the O&M Manual shall be submitted to the Department whenever they are incorporated into the manual. S6. PRETREATMENT A. General Requirements The Permittee shall work with the Department to ensure that all commercial and industrial users of the publicly owned treatment works (POTW) are in compliance with the pretreatment regulations promulgated in 40 CFR Part 403 and any additional regulations that may be promulgated under Section 307(b) (pretreatment) and 308 (reporting) of the Federal Clean Water Act. Page 18 of 35 Permit No. WA-002249-7 B. Wastewater Discharge Permit Required The Permittee shall not allow significant industrial users (SIUs) to discharge waste water to the Permittee's sewerage system until such user has received a wastewater discharge permit from the Department in accordance with Chapter 90.48 RCW and Chapter 173-216 WAC, as amended. C. Identification and Reporting of Existing, New, and Proposed Industrial Users 1. The Permittee shall take continuous, routine measures to identify all existing, new, and proposed SIUs and potential significant industrial users (PSIUs) discharging or proposing to discharge to the Permittee's sewerage system (see Appendix B of Fact Sheet for definitions). 2. Within thirty (30) days of becoming aware of an unpermitted existing, new, or proposed industrial user who may be an SIU, the Permittee shall notify such user by registered mail that, if classified as an SIU, they shall be required to apply to the Department and obtain a State Waste Discharge Permit. A copy of this notification letter shall also be sent to the Department within this same thirty (30)-day period. 3. The Permittee shall also notify all PSIUs, as they are identified, that if their classification should change to an SIU, they shall be required to apply to the Department for a State Waste Discharge Permit within thirty (30) days of such change. D. Industrial User Survey 1. The Permittee shall complete and submit to the Department an Industrial User Survey listing all SIUs and PSIUs discharging to the POTW. The survey shall be received by the Department by June 1, 2006. At a minimum, the list of SIUs and PSIUs shall be developed by means of a telephone book search, a water utility billing records search, and a physical reconnaissance of the service area. Information on PSIUs shall at least include: the business name, telephone number, address, description of the industrial process(es), and the known wastewater volumes and characteristics. For assistance with the development of the Industrial User Survey, the Permittee shall refer to the Department's guidance document entitled "Performing an Industrial User Survey." 2. The Permittee shall update the Industrial User Survey annually. The updated Industrial User Survey shall be received by the Department by June 1, 2007 and annually thereafter. The updated survey shall include a list of all new industrial users, as well as existing industrial users which are known or discovered to have significantly altered processes or disposal practices since submittal of the last survey or survey update. For industrial users for which there are potentially significant nondomestic discharges, the minimum information described in Section D.1, above, for PSIUs shall be obtained and included in the report. Page 19 of 35 Permit No. WA-002249-7 E. Duty to Enforce Discharge Prohibitions 1. In accordance with 40 CFR 403.5(a), the Permittee shall not authorize or knowingly allow the discharge of any pollutants into its POTW which cause pass-through or interference, or which otherwise violates general or specific discharge prohibitions contained in 40 CFR Part 403.5 or WAC-173-216-060. 2. The Permittee shall not authorize or knowingly allow the introduction of any of the following into their treatment works: a. Pollutants which create a fire or explosion hazard in the POTW (including, but not limited to waste streams with a closed cup flashpoint of less than 140 degrees Fahrenheit or 60 degrees Centigrade using the test methods specified in 40 CFR 261.21). b. Pollutants which will cause corrosive structural damage to the POTW, but in no case discharges with pH lower than 5.0, or greater than 11.0 standard units, unless the works are specifically designed to accommodate such discharges. c. Solid or viscous pollutants in amounts that could cause obstruction to the flow in sewers or otherwise interfere with the operation of the POTW. d. Any pollutant, including oxygen-demanding pollutants, (BOD, etc.) released in a discharge at a flow rate and/or pollutant concentration which will cause interference with the POTW. e. Petroleum oil, nonbiodegradable cutting oil, or products of mineral origin in amounts that will cause interference or pass-through. f. Pollutants which result in the presence of toxic gases, vapors, or fumes within the POTW in a quantity which may cause acute worker health and safety problems. g. Heat in amounts that will inhibit biological activity in the POTW resulting in interference but in no case heat in such quantities such that the temperature at the POTW headworks exceeds 40º C (104º F) unless the Department, upon request of the Permittee, approves, in writing, alternate temperature limits. h. Any trucked or hauled pollutants, except at discharge points designated by the Permittee. i. Waste waters prohibited to be discharged to the POTW by the Dangerous Waste Regulations (Chapter 173-303 WAC), unless authorized under the Domestic Sewage Exclusion (WAC 173-303-071). Page 20 of 35 Permit No. WA-002249-7 3. All of the following are prohibited from discharge to the POTW unless approved in writing by the Department under extraordinary circumstances (such as a lack of direct discharge alternatives due to combined sewer service or the need to augment sewage flows due to septic conditions): a. Noncontact cooling water in significant volumes. b. Stormwater, and other direct inflow sources. c. Wastewaters significantly affecting system hydraulic loading, which do not require treatment, or would not be afforded a significant degree of treatment by the system. 4. The Permittee shall notify the Department if any industrial user violates the prohibitions listed in this section. S7. RESIDUAL SOLIDS Residual solids include screenings, grit, scum, primary sludge, waste activated sludge, and other solid waste. The Permittee shall store and handle all residual solids in such a manner so as to prevent their entry into state ground or surface waters. The Permittee shall not discharge leachate from residual solids to state surface or ground waters. S8. ACUTE TOXICITY A. Effluent Limit for Acute Toxicity (Steamboat Slough discharge only) The effluent limit for acute toxicity is no acute toxicity detected in a test concentration representing the acute critical effluent concentration (ACEC). The ACEC means the maximum concentration of effluent during critical conditions at the boundary of the zone of acute criteria exceedance assigned pursuant to WAC 173-201A-100. The zone of acute criteria exceedance is authorized in Section S1.C. of this permit. The ACEC equals 9.2% effluent. In the event of failure to pass the test described in Subsection B of this section for compliance with the effluent limit for acute toxicity, the Permittee is considered to be in compliance with all permit requirements for acute whole effluent toxicity as long as the requirements in Subsection C are being met to the satisfaction of the Department. B. Monitoring for Compliance With an Effluent Limit for Acute Toxicity The Permittee shall conduct monitoring to determine compliance with the effluent limit for acute toxicity. The acute toxicity tests shall be performed using at a minimum 100% effluent, the ACEC, and a control. Acute toxicity testing shall follow protocols, monitoring requirements, and quality assurance/quality control procedures specified in this section. Testing shall begin in November 2005. A written report shall be submitted Page 21 of 35 Permit No. WA-002249-7 to the Department by December 15, 2005 and every three months (quarterly) thereafter except for the summer low-flow season (July-October). The percent survival in 100% effluent shall be reported along with all compliance monitoring results. Compliance monitoring shall be conducted quarterly using each of the species and protocols listed below on a rotating basis: 1) Fathead minnow, Pimephales promelas (96-hour static-renewal test, method: EPA/600/4-90/027F) 2) Daphnid, Ceriodaphnia dubia, Daphnia pulex, or Daphnia magna (48-hour static test, method: EPA/600/4-90/027F). The Permittee is in violation of the effluent limit for acute toxicity in Subsection A and shall immediately implement Subsection C if any acute toxicity test conducted for compliance monitoring determines a statistically significant difference in survival between the control and the ACEC using hypothesis testing at the 0.05 level of significance (Appendix H, EPA/600/4-89/001). If the difference in survival between the control and the ACEC is less than 10%, the hypothesis test shall be conducted at the 0.01 level of significance. C. Response to Noncompliance With an Effluent Limit for Acute Toxicity If a toxicity test conducted for compliance monitoring under Subsection B determines a statistically significant difference in response between the ACEC and the control, the Permittee shall begin additional compliance monitoring within one week from the time of receiving the test results. This additional monitoring shall be conducted weekly for four consecutive weeks using the same test and species as the failed compliance test. Testing shall be conducted using a series of at least five effluent concentrations and a control in order to be able to determine appropriate point estimates. One of these effluent concentrations shall equal the ACEC and be compared statistically to the nontoxic control in order to determine compliance with the effluent limit for acute toxicity as described in Subsection B. The discharger shall return to the original monitoring frequency in Subsection B after completion of the additional compliance monitoring. If the Permittee believes that a test indicating noncompliance will be identified by the Department as an anomalous test result, the Permittee may notify the Department that the compliance test result might be anomalous and that the Permittee intends to take only one additional sample for toxicity testing and wait for notification from the Department before completing the additional monitoring required in this subsection. The notification to the Department shall accompany the report of the compliance test result and identify the reason for considering the compliance test result to be anomalous. The Permittee shall complete all of the additional monitoring required in this subsection as soon as possible after notification by the Department that the compliance test result was not anomalous. If the one additional sample fails to comply with the effluent limit for acute toxicity, then the Permittee shall proceed without delay Page 22 of 35 Permit No. WA-002249-7 to complete all of the additional monitoring required in this subsection. The one additional test result shall replace the compliance test result upon determination by the Department that the compliance test result was anomalous. If all of the additional compliance monitoring conducted in accordance with this subsection complies with the permit limit, the Permittee shall search all pertinent and recent facility records (operating records, monitoring results, inspection records, spill reports, weather records, production records, raw material purchases, pretreatment records, etc.) and submit a report to the Department on possible causes and preventive measures for the transient toxicity event which triggered the additional compliance monitoring. If toxicity occurs in violation of the acute toxicity limit during the additional compliance monitoring, the Permittee shall submit a Toxicity Identification/Reduction Evaluation (TI/RE) plan to the Department within sixty (60) days after the sample date. The TI/RE plan shall be based on WAC 173-205-100(2) and shall be implemented in accordance with WAC 173-205-100(3). D. Sampling and Reporting Requirements 1. All reports for effluent characterization or compliance monitoring shall be submitted in accordance with the most recent version of Department of Ecology Publication # WQ-R-95-80, Laboratory Guidance and Whole Effluent Toxicity Test Review Criteria, in regards to format and content. Reports shall contain bench sheets and reference toxicant results for test methods. If the lab provides the toxicity test data on floppy disk for electronic entry into the Department’s database, then the Permittee shall send the disk to the Department along with the test report, bench sheets, and reference toxicant results. 2. Testing shall be conducted on 24-hour composite effluent samples. Samples taken for toxicity testing shall be cooled to 4 degrees Celsius while being collected and shall be sent to the lab immediately upon completion. The lab shall begin the toxicity testing as soon as possible but no later than 36 hours after sampling was ended. 3. All samples and test solutions for toxicity testing shall have water quality measurements as specified in Department of Ecology Publication # WQ-R-95-80, Laboratory Guidance and Whole Effluent Toxicity Test Review Criteria, or most recent version thereof. 4. All toxicity tests shall meet quality assurance criteria and test conditions in the most recent versions of the EPA manual listed in Subsection A and the Department of Ecology Publication # WQ-R-95-80, Laboratory Guidance and Whole Effluent Toxicity Test Review Criteria. If test results are determined to be invalid or anomalous by the Department, testing shall be repeated with freshly collected effluent. Page 23 of 35 Permit No. WA-002249-7 5. Control water and dilution water shall be laboratory water meeting the requirements of the EPA manual listed in Subsection A or pristine natural water of sufficient quality for good control performance. 6. The whole effluent toxicity tests shall be run on an unmodified sample of final effluent. 7. The Permittee may choose to conduct a full dilution series test during compliance monitoring in order to determine dose response. In this case, the series must have a minimum of five effluent concentrations and a control. The series of concentrations must include the ACEC. 8. All whole effluent toxicity tests, effluent screening tests, and rapid screening tests that involve hypothesis testing and do not comply with the acute statistical power standard of 29% as defined in WAC 173-205-020 must be repeated on a fresh sample with an increased number of replicates to increase the power. S9. CHRONIC TOXICITY A. Effluent Characterization The Permittee shall conduct chronic toxicity testing on the final effluent. The two chronic toxicity tests listed below shall be conducted on each sample taken for effluent characterization. Testing shall be conducted during November 2005 and May 2006. Written reports shall be submitted to the Department by December 15, 2005 and June 15, 2006. The Permittee shall conduct chronic toxicity testing during effluent characterization on a series of at least five concentrations of effluent in order to determine appropriate point estimates. This series of dilutions shall include the ACEC. The Permittee shall compare the ACEC to the control using hypothesis testing at the 0.05 level of significance as described in Appendix H, EPA/600/4-89/001. Chronic toxicity tests shall be conducted with the following two species and the most recent version of the following protocols: Saltwater Chronic Toxicity Test Species Method Topsmelt Atherinops affinis EPA/600/R-95/136 Mysid shrimp Holmesimysis costata or Mysidopsis bahia EPA/600/R-95/136 or EPA/600/4-91/003 The Permittee shall use the West Coast mysid (Holmesimysis costata) for toxicity testing unless the lab cannot obtain a sufficient quantity of a West Coast species in good condition in which case the East Coast mysid (Mysidopsis bahia) may be substituted. Page 24 of 35 Permit No. WA-002249-7 B. Effluent Limit for Chronic Toxicity (Steamboat Slough discharge only) After completion of effluent characterization, the Permittee has an effluent limit for chronic toxicity if any test conducted for effluent characterization shows a significant difference between the control and the ACEC at the 0.05 level of significance using hypothesis testing (Appendix H, EPA/600/4-89/001) and shall complete all applicable requirements in Subsections C, D, and F. If no significant difference is shown between the ACEC and the control in any of the chronic toxicity tests, the Permittee has no effluent limit for chronic toxicity and only Subsections E and F apply. The effluent limit for chronic toxicity is no toxicity detected in a test concentration representing the chronic critical effluent concentration (CCEC). In the event of failure to pass the test described in Subsection C, of this section, for compliance with the effluent limit for chronic toxicity, the Permittee is considered to be in compliance with all permit requirements for chronic whole effluent toxicity as long as the requirements in Subsection D are being met to the satisfaction of the Department. The CCEC means the maximum concentration of effluent allowable at the boundary of the mixing zone assigned in Section S1.C. pursuant to WAC 173-201A-100. The CCEC equals 3.7% effluent. C. Monitoring for Compliance with an Effluent Limit for Chronic Toxicity Monitoring to determine compliance with the effluent limit shall be conducted biannually for the remainder of the permit term using each of the species listed in Subsection A on a rotating basis and performed using at a minimum the CCEC, the ACEC, and a control. The Permittee shall schedule the toxicity tests in the order listed in the permit unless the Department notifies the Permittee in writing of another species rotation schedule. Compliance with the effluent limit for chronic toxicity means no statistically significant difference in response between the control and the test concentration representing the CCEC. The Permittee shall immediately implement Subsection D if any chronic toxicity test conducted for compliance monitoring determines a statistically significant difference in response between the control and the CCEC using hypothesis testing at the 0.05 level of significance (Appendix H, EPA/600/4-89/001). If the difference in response between the control and the CCEC is less than 20%, the hypothesis test shall be conducted at the 0.01 level of significance. In order to establish whether the chronic toxicity limit is eligible for removal from future permits, the Permittee shall also conduct this same hypothesis test (Appendix H, EPA/600/4-89/001) to determine if a statistically significant difference in response exists between the ACEC and the control. Page 25 of 35 Permit No. WA-002249-7 D. Response to Noncompliance With an Effluent Limit for Chronic Toxicity If a toxicity test conducted for compliance monitoring under Subsection C determines a statistically significant difference in response between the CCEC and the control, the Permittee shall begin additional compliance monitoring within one week from the time of receiving the test results. This additional monitoring shall be conducted monthly for three consecutive months using the same test and species as the failed compliance test. Testing shall be conducted using a series of at least five effluent concentrations and a control in order to be able to determine appropriate point estimates. One of these effluent concentrations shall equal the CCEC and be compared statistically to the nontoxic control in order to determine compliance with the effluent limit for chronic toxicity as described in Subsection C. The discharger shall return to the original monitoring frequency in Subsection C after completion of the additional compliance monitoring. If the Permittee believes that a test indicating noncompliance will be identified by the Department as an anomalous test result, the Permittee may notify the Department that the compliance test result might be anomalous and that the Permittee intends to take only one additional sample for toxicity testing and wait for notification from the Department before completing the additional monitoring required in this subsection. The notification to the Department shall accompany the report of the compliance test result and identify the reason for considering the compliance test result to be anomalous. The Permittee shall complete all of the additional monitoring required in this subsection as soon as possible after notification by the Department that the compliance test result was not anomalous. If the one additional sample fails to comply with the effluent limit for chronic toxicity, then the Permittee shall proceed without delay to complete all of the additional monitoring required in this subsection. The one additional test result shall replace the compliance test result upon determination by the Department that the compliance test result was anomalous. If all of the additional compliance monitoring conducted in accordance with this subsection complies with the permit limit, the Permittee shall search all pertinent and recent facility records (operating records, monitoring results, inspection records, spill reports, weather records, production records, raw material purchases, pretreatment records, etc.) and submit a report to the Department on possible causes and preventive measures for the transient toxicity event which triggered the additional compliance monitoring. If toxicity occurs in violation of the chronic toxicity limit during the additional compliance monitoring, the Permittee shall submit a Toxicity Identification/Reduction Evaluation (TI/RE) plan to the Department. The TI/RE plan submittal shall be within sixty (60) days after the sample date for the third additional compliance monitoring test. If the Permittee decides to forgo the rest of the additional compliance monitoring tests required in this subsection because one of the first two additional compliance monitoring tests failed to meet the chronic toxicity limit, then the Permittee shall submit the TI/RE plan within sixty (60) days after the sample date for the first additional monitoring test to violate the chronic toxicity limit. The TI/RE plan shall be based on WAC 173-205-100(2) and shall be implemented in accordance with WAC 173-205-100(3). Page 26 of 35 Permit No. WA-002249-7 E. Monitoring When There Is No Permit Limit for Chronic Toxicity The Permittee shall test final effluent during May 2009 and November 2009, prior to submission of the application for permit renewal. All species used in the initial chronic effluent characterization or substitutes approved by the Department shall be used and results submitted to the Department as a part of the permit renewal application process. F. Sampling and Reporting Requirements 1. All reports for effluent characterization or compliance monitoring shall be submitted in accordance with the most recent version of Department of Ecology Publication #WQ-R-95-80, Laboratory Guidance and Whole Effluent Toxicity Test Review Criteria, in regards to format and content. Reports shall contain bench sheets and reference toxicant results for test methods. If the lab provides the toxicity test data on floppy disk for electronic entry into the Department’s database, then the Permittee shall send the disk to the Department along with the test report, bench sheets, and reference toxicant results. 2. Testing shall be conducted on 24-hour composite effluent samples. Composite samples taken for toxicity testing shall be cooled to 4 degrees Celsius while being collected and shall be sent to the lab immediately upon completion. Grab samples must be shipped on ice to the lab immediately upon collection. If a grab sample is received at the testing lab within one hour after collection, it must have a temperature below 20° C at receipt. If a grab sample is received at the testing lab within 4 hours after collection, it must be below 12° C at receipt. All other samples must be below 8° C at receipt. The lab shall begin the toxicity testing as soon as possible but no later than 36 hours after sampling was ended. The lab shall store all samples at 4° C in the dark from receipt until completion of the test. 3. All samples and test solutions for toxicity testing shall have water quality measurements as specified in Department of Ecology Publication #WQ-R-95-80, Laboratory Guidance and Whole Effluent Toxicity Test Review Criteria, or most recent version thereof. 4. All toxicity tests shall meet quality assurance criteria and test conditions in the most recent versions of the EPA manual listed in Subsection A and the Department of Ecology Publication #WQ-R-95-80, Laboratory Guidance and Whole Effluent Toxicity Test Review Criteria. If test results are determined to be invalid or anomalous by the Department, testing shall be repeated with freshly collected effluent. 5. Control water and dilution water shall be laboratory water meeting the requirements of the EPA manual listed in Subsection A or pristine natural water of sufficient quality for good control performance. 6. The whole effluent toxicity tests shall be run on an unmodified sample of final effluent. Page 27 of 35 Permit No. WA-002249-7 7. The Permittee may choose to conduct a full dilution series test during compliance monitoring in order to determine dose response. In this case, the series must have a minimum of five effluent concentrations and a control. The series of concentrations must include the ACEC and the CCEC. 8. All whole effluent toxicity tests, effluent screening tests, and rapid screening tests that involve hypothesis testing, and do not comply with the chronic statistical power standard of 39% as defined in WAC 173-205-020, must be repeated on a fresh sample with an increased number of replicates to increase the power. S10. ADDITIONAL CHEMICAL ANALYSIS OF INFLUENT AND EFFLUENT A. Additional Effluent Testing To provide required data for EPA Form 3510-2A, Part B6 (NPDES application) for the next permit cycle, the following additional tests shall be conducted on the final plant effluent. Samples shall be collected for analysis annually during the term of this permit, and results shall be reported with the next NPDES permit application. Ammonia-N Chlorine (Total Residual, TRC) Dissolved Oxygen Total Kjeldahl Nitrogen NO3 + NO2-N Oil & Grease Total Phosphorus Total Dissolved Solids B. Priority Pollutant Scans The Permittee shall conduct annual priority pollutant scans of the influent and final treatment plant effluent. The samples analyzed shall be 24-hour composites. The parameters to be tested are listed in EPA Form 3510-2A, Part D (NPDES application). The results shall be submitted no later than forty-five (45) days following the monitoring period. The first submission shall be no later than December 15, 2005, and the results of all priority pollutant scans shall be submitted with the next NPDES permit application. C. Protocols Sample analysis shall be conducted in accordance with 40 CFR Part 136. D. Quality Assurance/Quality Control Procedures The Permittee shall follow the quality assurance procedures of 40 CFR Part 136. Page 28 of 35 Permit No. WA-002249-7 S11. OUTFALL EVALUATION The Permittee shall inspect the submerged portion of the Steamboat Slough outfall line and diffuser to document its integrity and continued function. If conditions allow for a photographic verification, it shall be included in the report. The inspection report shall be submitted to the Department by December 2009 along with the application for permit renewal. Page 29 of 35 Permit No. WA-002249-7 GENERAL CONDITIONS G1. SIGNATORY REQUIREMENTS All applications, reports, or information submitted to the Department shall be signed and certified. A. All permit applications shall be signed by either a principal executive officer or a ranking elected official. B. All reports required by this permit and other information requested by the Department shall be signed by a person described above or by a duly authorized representative of that person. A person is a duly authorized representative only if: 1. The authorization is made in writing by a person described above and submitted to the Department. 2. The authorization specifies either an individual or a position having responsibility for the overall operation of the regulated facility, such as the position of plant manager, superintendent, position of equivalent responsibility, or an individual or position having overall responsibility for environmental matters. (A duly authorized representative may thus be either a named individual or any individual occupying a named position.) C. Changes to authorization. If an authorization under paragraph B.2, above, is no longer accurate because a different individual or position has responsibility for the overall operation of the facility, a new authorization satisfying the requirements of paragraph B.2, above, must be submitted to the Department prior to or together with any reports, information, or applications to be signed by an authorized representative. D. Certification. Any person signing a document under this section shall make the following certification: “I certify under penalty of law, that this document and all attachments were prepared under my direction or supervision in accordance with a system designed to assure that qualified personnel properly gathered and evaluated the information submitted. Based on my inquiry of the person or persons who manage the system or those persons directly responsible for gathering information, the information submitted is, to the best of my knowledge and belief, true, accurate, and complete. I am aware that there are significant penalties for submitting false information, including the possibility of fine and imprisonment for knowing violations.” Page 30 of 35 Permit No. WA-002249-7 G2. RIGHT OF INSPECTION AND ENTRY The Permittee shall allow an authorized representative of the Department, upon the presentation of credentials and such other documents as may be required by law: A. To enter upon the premises where a discharge is located or where any records must be kept under the terms and conditions of this permit. B. To have access to and copy - at reasonable times and at reasonable cost - any records required to be kept under the terms and conditions of this permit. C. To inspect - at reasonable times - any facilities, equipment (including monitoring and control equipment), practices, methods, or operations regulated or required under this permit. D. To sample or monitor - at reasonable times - any substances or parameters at any location for purposes of assuring permit compliance or as otherwise authorized by the Clean Water Act. G3. PERMIT ACTIONS This permit may be modified, revoked and reissued, or terminated either at the request of any interested person (including the Permittee) or upon the Department’s initiative. However, the permit may only be modified, revoked and reissued, or terminated for the reasons specified in 40 CFR 122.62, 122.64 or WAC 173-220-150 according to the procedures of 40 CFR 124.5. A. The following are causes for terminating this permit during its term, or for denying a permit renewal application: 1. Violation of any permit term or condition. 2. Obtaining a permit by misrepresentation or failure to disclose all relevant facts. 3. A material change in quantity or type of waste disposal. 4. A determination that the permitted activity endangers human health or the environment, or contributes to water quality standards violations and can only be regulated to acceptable levels by permit modification or termination [40 CFR Part 122.64(3)]. 5. A change in any condition that requires either a temporary or permanent reduction, or elimination of any discharge or sludge use or disposal practice controlled by the permit [40 CFR Part 122.64(4)]. 6. Nonpayment of fees assessed pursuant to RCW 90.48.465. 7. Failure or refusal of the Permittee to allow entry as required in RCW 90.48.090. Page 31 of 35 Permit No. WA-002249-7 B. The following are causes for modification but not revocation and reissuance except when the Permittee requests or agrees: 1. A material change in the condition of the waters of the state. 2. New information not available at the time of permit issuance that would have justified the application of different permit conditions. 3. Material and substantial alterations or additions to the permitted facility or activities which occurred after this permit issuance. 4. Promulgation of new or amended standards or regulations having a direct bearing upon permit conditions, or requiring permit revision. 5. The Permittee has requested a modification based on other rationale meeting the criteria of 40 CFR Part 122.62. 6. The Department has determined that good cause exists for modification of a compliance schedule, and the modification will not violate statutory deadlines. 7. Incorporation of an approved local pretreatment program into a municipality’s permit. C. The following are causes for modification or alternatively revocation and reissuance: 1. Cause exists for termination for reasons listed in A1 through A7 of this section, and the Department determines that modification or revocation and reissuance is appropriate. 2. The Department has received notification of a proposed transfer of the permit. A permit may also be modified to reflect a transfer after the effective date of an automatic transfer (General Condition G8) but will not be revoked and reissued after the effective date of the transfer except upon the request of the new permittee. G4. REPORTING PLANNED CHANGES The Permittee shall, as soon as possible, but no later than sixty (60) days prior to the proposed changes, give notice to the Department of planned physical alterations or additions to the permitted facility, production increases, or process modification which will result in: 1) the permitted facility being determined to be a new source pursuant to 40 CFR 122.29(b); 2) a significant change in the nature or an increase in quantity of pollutants discharged; or 3) a significant change in the Permittee’s sludge use or disposal practices. Following such notice, and the submittal of a new application or supplement to the existing application, along with required engineering plans and reports, this permit may be modified, or revoked and reissued pursuant to 40 CFR 122.62(a) to specify and limit any pollutants not previously limited. Until such modification is effective, any new or increased discharge in excess of permit limits or not specifically authorized by this permit constitutes a violation of the terms and conditions of this permit. Page 32 of 35 Permit No. WA-002249-7 G5. PLAN REVIEW REQUIRED Prior to constructing or modifying any wastewater control facilities, an engineering report and detailed plans and specifications shall be submitted to the Department for approval in accordance with Chapter 173-240 WAC. Engineering reports, plans, and specifications shall be submitted at least one hundred and eighty (180) days prior to the planned start of construction unless a shorter time is approved by Ecology. Facilities shall be constructed and operated in accordance with the approved plans. G6. COMPLIANCE WITH OTHER LAWS AND STATUTES Nothing in this permit shall be construed as excusing the Permittee from compliance with any applicable federal, state, or local statutes, ordinances, or regulations. G7. DUTY TO REAPPLY The Permittee shall apply for permit renewal at least one hundred and eighty (180) days prior to the specified expiration date of this permit. G8. TRANSFER OF THIS PERMIT In the event of any change in control or ownership of facilities from which the authorized discharge emanate, the Permittee shall notify the succeeding owner or controller of the existence of this permit by letter, a copy of which shall be forwarded to the Department. A. Transfers by Modification Except as provided in paragraph (B) below, this permit may be transferred by the Permittee to a new owner or operator only if this permit has been modified or revoked and reissued under 40 CFR 122.62(b)(2), or a minor modification made under 40 CFR 122.63(d), to identify the new Permittee and incorporate such other requirements as may be necessary under the Clean Water Act. B. Automatic Transfers This permit may be automatically transferred to a new permittee if: 1. The Permittee notifies the Department at least thirty (30) days in advance of the proposed transfer date. 2. The notice includes a written agreement between the existing and new Permittees containing a specific date transfer of permit responsibility, coverage, and liability between them. 3. The Department does not notify the existing Permittee and the proposed new Permittee of its intent to modify or revoke and reissue this permit. A modification under this subparagraph may also be minor modification under 40 CFR 122.63. If this notice is not received, the transfer is effective on the date specified in the written agreement. Page 33 of 35 Permit No. WA-002249-7 G9. REDUCED PRODUCTION FOR COMPLIANCE The Permittee, in order to maintain compliance with its permit, shall control production and/or all discharges upon reduction, loss, failure, or bypass of the treatment facility until the facility is restored or an alternative method of treatment is provided. This requirement applies in the situation where, among other things, the primary source of power of the treatment facility is reduced, lost, or fails. G10. REMOVED SUBSTANCES Collected screenings, grit, solids, sludges, filter backwash, or other pollutants removed in the course of treatment or control of wastewaters shall not be resuspended or reintroduced to the final effluent stream for discharge to state waters. G11. DUTY TO PROVIDE INFORMATION The Permittee shall submit to the Department, within a reasonable time, all information which the Department may request to determine whether cause exists for modifying, revoking and reissuing, or terminating this permit or to determine compliance with this permit. The Permittee shall also submit to the Department upon request, copies of records required to be kept by this permit. G12. OTHER REQUIREMENTS OF 40 CFR All other requirements of 40 CFR 122.41 and 122.42 are incorporated in this permit by reference. G13. ADDITIONAL MONITORING The Department may establish specific monitoring requirements in addition to those contained in this permit by administrative order or permit modification. G14. PAYMENT OF FEES The Permittee shall submit payment of fees associated with this permit as assessed by the Department. G15. PENALTIES FOR VIOLATING PERMIT CONDITIONS Any person who is found guilty of willfully violating the terms and conditions of this permit shall be deemed guilty of a crime, and upon conviction thereof shall be punished by a fine of up to ten thousand dollars ($10,000) and costs of prosecution, or by imprisonment in the discretion of the court. Each day upon which a willful violation occurs may be deemed a separate and additional violation. Any person who violates the terms and conditions of a waste discharge permit shall incur, in addition to any other penalty as provided by law, a civil penalty in the amount of up to ten thousand dollars ($10,000) for every such violation. Each and every such violation shall be a separate and distinct offense, and in case of a continuing violation, every day's continuance shall be deemed to be a separate and distinct violation. Page 34 of 35 Permit No. WA-002249-7 G16. UPSET Definition – “Upset” means an exceptional incident in which there is unintentional and temporary noncompliance with technology-based permit effluent limitations because of factors beyond the reasonable control of the Permittee. An upset does not include noncompliance to the extent caused by operational error, improperly designed treatment facilities, inadequate treatment facilities, lack of preventive maintenance, or careless or improper operation. An upset constitutes an affirmative defense to an action brought for noncompliance with such technology-based permit effluent limitations if the requirements of the following paragraph are met. A Permittee who wishes to establish the affirmative defense of upset shall demonstrate, through properly signed, contemporaneous operating logs, or other relevant evidence that: 1) an upset occurred and that the Permittee can identify the cause(s) of the upset; 2) the permitted facility was being properly operated at the time of the upset; 3) the Permittee submitted notice of the upset as required in Condition S3.E; and 4) the Permittee complied with any remedial measures required under S4.C of this permit. In any enforcement proceeding, the Permittee seeking to establish the occurrence of an upset has the burden of proof. G17. PROPERTY RIGHTS This permit does not convey any property rights of any sort, or any exclusive privilege. G18. DUTY TO COMPLY The Permittee shall comply with all conditions of this permit. Any permit noncompliance constitutes a violation of the Clean Water Act and is grounds for enforcement action; for permit termination, revocation and reissuance, or modification; or denial of a permit renewal application. G19. TOXIC POLLUTANTS The Permittee shall comply with effluent standards or prohibitions established under Section 307(a) of the Clean Water Act for toxic pollutants within the time provided in the regulations that establish those standards or prohibitions, even if this permit has not yet been modified to incorporate the requirement. G20. PENALTIES FOR TAMPERING The Clean Water Act provides that any person who falsifies, tampers with, or knowingly renders inaccurate any monitoring device or method required to be maintained under this permit shall, upon conviction, be punished by a fine of not more than $10,000 per violation, or by imprisonment for not more than two (2) years per violation, or by both. If a conviction of a person is for a violation committed after a first conviction of such person under this Condition, punishment shall be a fine of not more than $20,000 per day of violation, or by imprisonment of not more than four (4) years, or by both. Page 35 of 35 Permit No. WA-002249-7 G21. REPORTING ANTICIPATED NONCOMPLIANCE The Permittee shall give advance notice to the Department by submission of a new application or supplement thereto at least one hundred and eighty (180) days prior to commencement of such discharges, of any facility expansions, production increases, or other planned changes, such as process modifications, in the permitted facility or activity which may result in noncompliance with permit limits or conditions. Any maintenance of facilities, which might necessitate unavoidable interruption of operation and degradation of effluent quality, shall be scheduled during noncritical water quality periods and carried out in a manner approved by the Department. G22. REPORTING OTHER INFORMATION Where the Permittee becomes aware that it failed to submit any relevant facts in a permit application, or submitted incorrect information in a permit application, or in any report to the Department, it shall promptly submit such facts or information. G23. COMPLIANCE SCHEDULES Reports of compliance or noncompliance with, or any progress reports on, interim and final requirements contained in any compliance schedule of this permit shall be submitted no later than fourteen (14) days following each schedule date. APPENDIX B CITY OF MARYSVILLE AGREEMENTS APPENDIX C PUMP STATION INVENTORY PUMP STATION INVENTORY Sunnyside Pump Station - 6213 - 52nd Street NE, Marysville, Washington PUD Meter No. 126280 Wet well – approx. one day between pump starts at this time. Main Electrical Panel, Cutler Hammer – Freedom Series 2100 Motor Control Center. HSE 39462-002/P0C 12/99 H.BUS 600A/65 480V 3PH 3W 60HZ SEC. 3-4 300A Main 400A Pump Controls – Superior Custom Controls PUMPS – THREE Wemco – Hydrostal Screw Centrifugal Pumps 1 and 2, 890 GPM, Head 53.3 ft., RPM 1750 6x5 model – E5K-EEXR4 Wemco Ser. No. 99X21929, 99X21930 Pump 3, Small original pump replaced in 2010. 6X5 Model-M_EEXR4 Ser. No. 0DW07608-01 1730 RPM 920GPM @ 50 ft. TDH High Crome Liner (regulable) MOTORS – THREE 20.7 HP., 1728 RPM, 460-VOLTS Model No. EEXR4-MYAK-XBLB-16 F.L. amps 27, HZ – 60, PH 3 S.F.I.O. Part No. 126317XP Back Up Generator Model No. OTC-3383933 Ser. No. J990008806 SPEC-K Amps – 400 VOLTAGE – 480 Frequency – 60 Poles – 4 Transfer Switch Valves P/N – 0306-3479-03 5 – 10 INCH CLOW 175 C W P MAX-AC VOLTS – 600 1 – 6 INCH CLOW 175 C W P PH 1 OR 3 1 – 12 INCH CLOW 175 C W P HZ 50 OR 60 2 – 10 INCH KENNEDY CHECK VALVES AC AMP CONT. – 150 1 – 6 INCH KENNEDY CHECK VALVE OPR. VOLTS – 208/220/240 POLES - 3 7/20/11 PUMP STATION INVENTORY Soper Hill Pump Station - 6914 Sunnyside Blvd, Marysville, Washington PUD meter no. 126675 Controls – Superior Custom Control’s. 12544 27th Ave N.E. Seattle, WA. 98125 Telephone, (206) 362 8866 On Site Generator, ONAN. Mod. No. DGFB-5564206 Ser. No. GO20391069 3 PH. 175 KW. RATED KVA 218.7 Transfer Switch, ONAN. Mod. No. OTPCC-5564280. Ser. No. GO20392624 Milltronics Multiranger Plus. PUMPS-TWO WEMCO-HYDROSTAL SCREW CENTRIFUGAL PUMP 8X4 Model F4K-S-FE5B5 Ser. No. (S) O2DWO3680-01,-02 Address, WEMCO PUMP 440 West 800 South Salt Lake City, UT 84101 Telephone, (801) 359-8731 Local Rep. APSCO 935 Kirkland Ave. Suite # 3. Kirkland, Wa 98033 (425) 822-3335 WEMCO MOTOR-Wemco Hydrostal immersible motor Model: FE5B5 60.4/20.9 HP, 1750/1150 RPM 3 PH. 60 HZ 460 VOLTS Fiberglass prerotation basin, size 800 Discharge 6 in. D.I. pipe too valve vault, 6 in. swing checks (2), Clow, Mod: 106, 6 in. Millcentric plug valves (2), series 600. No drain in valve vault Meter vault, Two Milliken 10 in. 285 CWP DI valves. Flow Meter, Danfoss Magflow. Sump pump in vault. 7/20/11 !"#$%"&&’ ’(&&%) &*#*&& !"! #$%$&!#’(" &$)*+ #$%$,-$* +#&& ""./"0 !12 &#$+""3 " %( ’45 6 "4 /0 "!- ##(#)-6 -()+7 4 8 $9! +0 8 :(6 ,$! !-5 +9 8,-&$9 !;#-, 4’< #% ’45-6 "="8 "8()+7 #6 !>/""1 ! &!7$6? $,*" <$ &"%&# 6 $"/0 <"< #)@ <"< #0 = >""@ ,+,-./.0’.1 2 3 "="/="0 - PUMP STATION INVENTORY Quilceda Glen Pump Station - 11910 - 51st Avenue NE, Marysville, WA. P.U.D. Meter No. 485639 P.U.D. Account # 450033638 Wet well – 72 in. X 11 ft. Only able to use 10 in. of well. Even 10 in. surcharges an already short collection system. Minimal retention time. Main Electrical and control’s – Calvert Technologies. 2 Cutler Hamer disconnects, 230 volt, 30 amp. Pumps controlled by Milltronics Hydroranger Pumps – Two Hydromatic HP. 2 Model No. S4NX200CB Ser. No. 508542 Phase 1, Volts 230, HZ 60. FLA 16.2 Back Up - Portable Generator Appleton male receptacle AR200 34RS Cutler Hamer double throw safety switch, 60 amp, 250 volt. Valves, in vault. 2 check valves – Clow Kennedy 4 in. 11071 2 gate valves – Mueller 4 in. 2360 AWWA 250W All pipe and fittings in vault are 4-in. ductile iron. PUMP STATION INVENTORY Marysville West Pump Station - 2510 Marine View Drive, Marysville, Washington. Wet Well: Retention time approximately 16 hours till overflow to Sturgeon Creek. Main Electrical Panel: Square D. Control Panel: Superior Custom Controls PUMPS – 2 FAIRBANKS MORSE Stage 1 Size 6 Model – 5413B28 Imp. 10 Total H.D. 23 ft. Serial Number K2N0152370 RPM: 1150 GPM: 1150 MOTORS – 2 GENERAL ELECTRIC Model Number SK6236XH205B Horsepower: 10 Type K Code H Frame: 256TP10 Nema Class B Volts: 230 / 460 Cycles: 60 3PH. F.L. Amps: 29 / 14.5 F.L. Speed: 1165 60C Rise Continuous No. JDJ925367 Upper Bearing: 590-3493P11 Lower Bearing: 629-A310FLP1 Back Up – Portable Generator PUMP STATION INVENTORY Kellogg Ridge Pump Station – 6623 - 105th Street NE, Marysville, Washington Wet well size – 72 inches x 14 ft Retention Time – Unknown. Main electrical panel, Square D – 100 amp, 480 volt. Cat. No. NF412L1C Pump Controls-Systems Interface Inc. 480 volt 3-PH 1—45 amp main breaker, Siemens- cat. No. ED43BO45 2—20 amp pump breakers, Siemens- cat. No. ED43BO20 Control panel—Systems Interface Inc. Rugid Telemetry Milltronics Transducer Pumps – Two Hydromatic – S4PX Back Up – Portable Generator Transfer Switch- Midwest Check Valves in vault- 2 Mueller 4 in. 175 WP Isolation Valves- 2 Milliken 4 in. 175 CWP DI PUMP STATION INVENTORY Ebey Slough Waterfront Park PUD METER NO. 509747 Wet Well Size—5’W X 9’ D Electrical Panel—Square “D” Control Panel -Pentiar Pumps Control Model 6204E01149937 Ashland Ohio 419-298-3042 Pumps—Two Hydromatic-Grinder Model No. HPGFHX300JC Ser. No. G82806 Hp. 3, Volts/460/PH 3 RPM 1750 FLA 4.8 SFA 5.6 CL.ins-F / code B / Temp code T.4 Imp 7.46 / BC-O MFG date 11-04 Motor model No. GA8X300JC Valves—two Brass wheel valves six feet down in earth on PVC force main w/valve stacks. Force main is 2 ½ in. PVC too man hole at 1st St. !"#$%&#’()*++,* ($*-.. +*’$$*-+ ,.’ ’’ !" # # ## $%! %% /$/&#’(%%%)*+ ,&#’(%-./0/1/2.3445$6 7 7 */ ,#*%&#’8)*9 +: $3 %1 :;;6 %0 # 6 <=,1*34 -6$6 $ / + >0 *6 / 5 $+ 76 +6?5 1 -$0/.. &%0 *& )!/1 &%4 =@ AB--B <$ &%4 =@ /A;B 1!#!C 3 )10 . /1 7 ! D /D PUMP STATION INVENTORY Cedar Crest Vista Pump Station Address – 8102 67th Ave. N.E. PUD Meter No. – 438729 Wet Well – 72 in. X 20 ft. 12 – 16 hr. retention time. Electrical – USEMCO Control Panel No. 14843 P.O. Box 583 Tomah, Wisconsin Telemetry – Systems Interface, Allen Bradley, Siemens Hydroranger 200. Pumps – 2- upgraded March 2008 WEMCO HYDROSTAL – with prerotation basins, size 600 4X4 Model D3K-S DKXA4 Ser, No. 07DW06595-01,-02 150 GPM @ 40 ft. TDH, at 1755 rpm. CW viewed from top of motor. Motor – Wemcp-Hydrostal imersible Model DK4A4, 7.9 hp. 3 ph, 60 HZ, 460 V. Valves, in vault. Check valves – 2 Muller 4 in. 1996 175 WP, Chat. Tenn. Control Valves – 3 Gate Valves, Muller 86, 4 in. A2360, AWWA 250W, 200 (FM) 7/21/11 PUMP STATION INVENTORY Carroll’s Creek Pump Station - 18111 - 25th Avenue NE, Arlington, WA. PUD meter no. 482462 Wet well 10ft.X 24ft. Approx. 4 hr. retention time. Without power. Main Control panel – Superior Custom Controls Milltronics Multiranger Plus PUMPS – TWO HYDROMATIC – submersible Model: S4PX750FC Type: non-clog 4in. HP. 7.5 Phase: 3 Voltage: 460 Pump speed: 1750 RPM. Frequency: 60 HZ. VALVES Two – CAM-CETRIC plug valves 4 in. Valmatic-CWP PSI 175 Mod. No. 5804RN Ser. No. M218510 Two – WATEROUS check valves 4 in. 604 175-W Ventilation Blower in valve vault Dayton 13X11/16 in. Mod. No. 3C494B Back Up – Portable Generator Transfer Switch – Cuttler Hammer !"# $ %&’(&) **++!,)#-.! +//+! +! !"!#$%& !0 ’(’)*+,, !- !.!+ "’ /’"0#/"1 2-$’ + !+!0 1$/2 + !345 6 +)..)78 22 -2 +3 + !7 1($+ ’!9 -09 $ 4 /2 !’!,:! PUMP STATION INVENTORY 88th Street Pump Station – 3801 - 88th Street NE, Marysville, Washington PUD Meter No. 420444 Wet well - 12-20 hr. retention time 96 in. X 15 ft. Main Electrical – International Control Systems 1911 61st Ave. N.E. Arlington WA 98223 Hydroranger Plus (Milltronics) PUMPS – 2 FLYGT – 3127.090 – 1025 15 9810089 484 FLS M21 – 12 – 4AL Y ser/ Y11 7.5 KW – 10hp. Cos 0.89 460/230 V 13/25 A 1735R/min VALVES – in vault Check Valves – 2, Mueller 6 in. 175WP 2 – Kestone Ballcentric 6 in. All pipe and fittings in vault – 6 in. ductile. BACK UP GENERATOR – F. G. WILSON Type – P95E Ser. No. – K3320A/001 KVA 112.5 Volts – 240/120 KW – 90 Amps – 270.6 HZ – 60 PF – 0.8 RPM – 1800 Phase – 3 STAT. CON. S/DELTA Amb. Temp. – 30 C VENTALATION FAN Blower 3C494 3-11/16 in. diameter Daton motor- Mod. # 3K0390 ½ HP. AMPS 9.0/4.5 VOLTS 113/230 RPM 1725 TRANSFER SWITCH Service, 1-800-800-ASCO ASCO automatic switch co. Florham Park, N.J. 07932 104 amps 480 volts 60 Hz. 3 phase Cat. No. A300310491C BOM 601351-003 Control Pnl. 473670-006 Wiring Dwg. 493577 PUMP STATION INVENTORY 51st Pump Station - 12209 - 51st Avenue NE, Marysville, Washington PUD Meter No. - 498763 Wet well – approx. 30-min. storage time after high water alarm before overflow to Quilceda creek. Control panel- TESCO 480 V, 3 phase, 200 amp, HZ 60. Telemetry- Radio/Alan Bradley. PUMPS – THREE WEMCO HYDROSTAL—PREROTATION 10X10 MODEL F10K-SS-FE457 Ser. No. 03DW04146-01,-02,-03. Conditions: 3100/600 GPM Against: 22’/24’ TDH At: 1170/870 RPM MOTORS THREE WEMCO-HYDROSTAL Immersible Motor MODEL FE547 29.5/14.7 HP, 1150/870 RPM 3 PHASE, 60 HZ, 230/460 VOLT SF 1.0 VALVES 3 check valves – in vault-12” WATEROUS 612 175-W 4 12” plug valves downstream, buried, between check valves and meter. 1 16” plug valve buried downstream of meter. FLOW METER In Vault DANFOSS-SITRANS FM MAG FLOW-MAG 3100 Signal Converter-MAG 5000 MILLTRONICS HYDRORANGER 200 BACK UP GENERATOR – F.G. WILSON, PERKINS DEISEL Type P 180 Ser. No. X3320B/001 KVA 225 Volts 480/277 KW 180 , Amps 270.6 HZ 60 , P.F. 0.8 RPM 1800 , Phase 3 Stat. Con. S/STAR amb. Temp. 30 C TRANSFER SWITCH LAKE SHORE ELECTRIC Trans-o-matic Ser. No. 931-0833 Part No. 17330400 Amps 400, Volts 480 Ph. 3, wire 4, HZ 60 PUMP STATION INVENTORY 3rd Street Pump Station – 4932 - 61st Street NE, Marysville, Washington PUD Meter No. 439162 Wet well – 24-hr. capacity without power. Electrical – Superior Custom Controls Telemetry – Rugid, Circuit No. VMNA .31810 A04 PUMPS – 2 FLIGT – submersible, 3 hp. Product no. 3085. 092 – 6011 Factory code. 15 Serial No. 9730364 Curve code, first didgit=number of poles, 440 Motor No. M15 – 10 – 4AL Stator con. YSER/Y/ Shaft Power, 2.2 KW - 3 HP Power Factor, 0.83 Rated Voltage, 460/230 Rated Current, 4.3/8.7 Number of Phases, type of current, frequency 3-60 Operating duty, cont./int. S1 % Rated speed, 1700 rpm VALVES, - in vault. Check valves – 2 Hillen DE Lelie, DN 100 4in. 2 - Millikin 4in. 175CWP A126 CLB All pipe and fittings in vault, 4in. ductile Back Up – Portable Generator PUMP STATION INVENTORY West Trunk Pump Station Wet Well Size-45’X12’-9”x24’ deep Electrical controls-GE 8000 – 600 A 480 V 3 Phase Pumps – Three – in dry pit. Wemco Hydrostal Mod. E8K-HD-EE324 Ser. No. 9311624-1,2,3. Motor Mod. EE3Z4-MXA-Y23C-16 Hp. 25.5 RPM 1748 Volts 460 FLA 41.5 HZ 60 SF 1.0 Isolation Valves DeZerik 16” plug valves, three, Part no. 9253145 DeZerik 12” plug valves, three, Part no. 9253148 Check valves MH 12”, three, 412095 Backup generator Cummins/Onan Generator Set Model: 125 DGEA S/N C940538066 Transfer Switch Onan Model: OTCU 225G Meter-Siemens MAGFLOW MAG 5100 W Inverter –Siemens SITRANS FM MAGFLOW MAG 6000 APPENDIX D LAND USE DATA/LOADING TABLES Marysville Sewer Comprehensive Plan 2011 Sewer Sub-Basin Land Use Sub-Basin Single Family Residential Dwelling Units Multi Family Residential Dwelling Units Commercial (acres) Non-Sewered Single Family Residential Dwelling Units Non-Sewered Multi Family Residential Dwelling Units Non-Sewered Commercial (acres) A1 0 0 11.1 1 0 0.0 A10 202 0 0.0 33 16 0.0 A11 117 4 3.1 2 0 0.0 A12 181 0 0.0 44 0 0.0 A12-1 116 3 0.0 4 0 0.0 A12-2 267 0 0.0 13 0 0.0 A12-3 145 0 0.0 0 0 0.0 A12-4 97 0 0.0 9 0 0.0 A13 265 2 2.4 17 0 0.0 A14 66 0 0.0 25 0 0.0 A15 128 0 0.0 3 0 0.0 A16 98 13 0.0 65 0 8.4 A16-1 163 0 0.0 113 0 0.0 A17 78 8 0.6 65 0 0.0 A18 205 0 0.0 7 0 0.0 A18-1 6 0 0.0 102 0 0.0 A18-2 101 0 0.0 0 0 0.0 A18-3 50 0 0.0 17 0 0.0 A19 228 0 0.0 196 0 0.0 A2 18 155 1.0 2 0 0.0 A20 261 2 0.0 74 0 0.0 A21 86 0 56.5 7 0 0.0 A22 167 0 1.7 96 0 0.0 A23 167 31 0.5 6 0 0.0 A24 263 34 0.0 0 0 0.0 A24-1 2 0 1.0 1 0 0.0 A24-2 0 0 0.0 0 0 0.0 A24-3 0 0 0.0 0 0 0.0 A24-4 63 180 18.0 1 1 0.0 A24-5 2 0 0.0 4 0 0.0 A25 2 0 0.0 2 0 0.0 A25-1 2 0 0.0 1 0 0.0 A26 18 0 8.5 2 0 5.0 A27 5 0 31.7 3 0 5.4 A28 138 0 0.0 101 0 0.0 A4 83 57 0.7 31 6 0.0 A5 61 155 0.5 53 0 0.0 A6 202 330 2.2 185 10 1.0 A7 86 4 0.2 95 0 0.0 A8 77 6 3.4 50 14 0.0 A9 61 0 8.4 20 0 0.0 B1 105 75 7.5 177 4 2.4 B2 0 0 0.0 119 0 0.0 B3 52 7 6.5 44 18 0.0 B4 19 0 0.0 60 0 0.0 B5 12 0 0.0 58 0 0.0 CE1 42 4 0.0 26 3 0.0 P. 1 M:\MARYSVILLE\11447_Sewer_Comp_Plan\ Appendices\Appx F Land Use Table.xls Marysville Sewer Comprehensive Plan 2011 Sewer Sub-Basin Land Use Sub-Basin Single Family Residential Dwelling Units Multi Family Residential Dwelling Units Commercial (acres) Non-Sewered Single Family Residential Dwelling Units Non-Sewered Multi Family Residential Dwelling Units Non-Sewered Commercial (acres) CE2 66 26 0.2 93 0 0.0 CE3 94 0 0.0 30 0 0.0 CE4 62 0 0.0 13 0 0.0 CE5 43 0 0.0 65 0 0.0 CE5-1 72 0 0.0 1 0 0.0 CE5-2 0 130 99.4 0 0 0.0 CE5-3 228 6 0.0 6 0 0.0 CE5-4 38 0 3.1 0 0 3.9 CE5-5 27 28 0.0 1 0 0.0 CE5-6 78 0 0.0 0 0 0.0 CE5-7 433 0 14.1 53 0 0.0 CE6 152 0 0.0 53 0 0.0 CE7 258 0 0.0 5 0 0.0 CE8 124 0 0.0 0 0 0.0 CE9 115 0 0.0 3 0 0.0 CW1 283 189 48.0 44 13 0.0 CW10 124 2 1.7 72 0 3.4 CW11 14 0 15.6 100 0 0.0 CW11-1 35 0 28.1 347 0 0.0 CW12 41 3 18.6 34 0 4.3 CW13 35 95 33.3 22 0 0.0 CW14 45 28 17.4 52 8 0.0 CW15 20 1 3.8 537 13 5.8 CW2 144 31 10.6 1 0 0.5 CW3 241 100 9.0 1 0 0.0 CW4 36 126 30.1 2 18 2.7 CW5 2 6 25.5 1 0 0.1 CW6 24 282 3.1 19 5 0.6 CW7 79 37 34.1 3 0 2.6 CW8 120 160 24.4 18 0 0.1 CW9 1 0 15.4 0 0 1.1 D1 24 10 4.1 14 0 0.0 D10 96 0 0.0 0 0 0.0 D10-1 0 0 0.0 38 0 6.2 D10-2 130 0 0.0 55 0 0.0 D10-3 0 0 0.0 36 0 0.0 D10-4 0 0 0.0 44 0 0.0 D10-5 0 0 0.0 12 0 0.0 D10-6 167 0 0.0 58 40 0.0 D11 73 0 0.0 0 0 0.0 D12 226 0 0.0 0 0 0.0 D2 50 0 0.0 1 0 0.0 D3 85 0 5.7 4 0 0.0 D3-1 137 3 0.0 3 0 0.0 D3-10 250 8 0.0 7 0 0.0 D3-11 414 0 0.0 17 0 0.0 D3-12 388 2 0.0 71 0 0.0 P. 2 M:\MARYSVILLE\11447_Sewer_Comp_Plan\ Appendices\Appx F Land Use Table.xls Marysville Sewer Comprehensive Plan 2011 Sewer Sub-Basin Land Use Sub-Basin Single Family Residential Dwelling Units Multi Family Residential Dwelling Units Commercial (acres) Non-Sewered Single Family Residential Dwelling Units Non-Sewered Multi Family Residential Dwelling Units Non-Sewered Commercial (acres) D3-13 50 0 0.0 41 0 0.0 D3-2 133 0 0.0 1 0 0.0 D3-3 111 0 0.0 7 0 0.0 D3-4 81 4 0.0 16 0 0.0 D3-5 523 1 3.5 57 1 0.0 D3-6 41 1 0.0 17 1 0.0 D3-7 127 0 0.0 14 0 0.0 D3-8 460 0 0.0 2 0 0.0 D3-9 252 0 0.0 3 0 0.0 D4 140 1 0.0 1 1 0.0 D5 183 0 3.3 11 0 0.0 D5-1 0 0 6.1 0 0 0.0 D5-2 181 203 6.1 3 0 0.0 D6 211 0 0.0 3 0 0.0 D6-1 88 0 0.0 1 0 0.0 D6-2 752 0 3.2 19 0 0.0 D6-3 97 2 0.0 1 0 0.0 D6-4 157 0 0.0 1 0 0.0 D6-5 263 0 0.0 7 0 0.0 D7 49 0 0.0 4 0 0.0 D7-1 133 0 0.0 0 0 0.0 D7-2 146 0 0.0 0 0 0.0 D8 52 0 2.8 2 0 0.0 D9 145 0 0.0 3 0 0.0 D9-1 122 0 0.0 2 0 0.0 F1 7 0 0.0 19 0 0.0 F10 0 0 50.6 1 0 21.5 F11 1 0 23.3 0 0 0.0 F12 4 0 50.8 2 0 5.7 F13 1 0 35.9 0 0 0.0 F13-1 0 0 1.0 3 0 0.0 F13-2 36 0 0.0 3 0 0.0 F14 11 0 35.1 18 0 0.0 F15 83 0 34.1 4 0 0.0 F16 2 4 9.2 0 0 13.8 F17 4 0 20.9 9 0 0.0 F18 0 0 26.3 0 0 0.0 F19 0 0 48.5 0 0 0.0 F2 13 0 0.0 110 0 0.0 F20 160 42 52.7 1 0 0.0 F21 249 293 1.8 8 0 0.0 F22 26 75 30.4 197 14 0.0 F22-1 0 0 2.5 44 0 22.8 F3 69 18 0.0 0 0 0.0 F4 240 0 0.0 73 0 0.0 F5 22 58 18.5 28 0 0.0 F6 45 0 0.0 0 0 0.0 P. 3 M:\MARYSVILLE\11447_Sewer_Comp_Plan\ Appendices\Appx F Land Use Table.xls Marysville Sewer Comprehensive Plan 2011 Sewer Sub-Basin Land Use Sub-Basin Single Family Residential Dwelling Units Multi Family Residential Dwelling Units Commercial (acres) Non-Sewered Single Family Residential Dwelling Units Non-Sewered Multi Family Residential Dwelling Units Non-Sewered Commercial (acres) F7 21 0 15.1 11 0 0.0 F8 5 6 9.5 5 0 0.0 F9 0 0 19.0 0 0 0.0 G1 93 93 31.4 4 3 0.6 G2 121 104 6.4 44 10 0.0 G3 1 0 76.9 0 0 0.0 G4 0 0 22.5 10 0 0.0 G5 144 0 0.0 0 0 0.0 G6 130 0 0.0 0 0 0.0 G7 3 0 0.0 63 0 28.8 G8 0 0 11 10 0 0 Total:15,569 3,248 1,269 4,753 199 147 P. 4 M:\MARYSVILLE\11447_Sewer_Comp_Plan\ Appendices\Appx F Land Use Table.xls Marysville 2011 Sewer Sub-Basin Flows BASINS (service area) Sewered Single Family Units Sewered Multi Family Units Single Family Population on Sewer Multi-Family Population on Sewer Total Existing Population On Sewer Residential Wastewater Flow (gpd) School Population School Wastewater Flow (gpd) Area (acres) Average Flow (gpd) Area (acres) Peak I/I Flow (gpd)Remark A1 0 0 0 0 0 0 0 11.1 30,034 0 11.1 12,206 0 A10 202 0 606 0 606 36,360 626 6,260 0.0 0 42,620 46.0 50,651 0 A11 117 4 351 8 359 21,540 0 3.1 8,239 21,540 16.7 18,365 0A121810543054332,580 0 0.0 0 32,580 32.6 35,901 0 A12-1 116 3 348 6 354 21,240 0 0.0 0 21,240 19.9 21,924 0 A12-2 267 0 801 0 801 48,060 0 0.0 0 48,060 31.7 34,898 0 A12-3 145 0 435 0 435 26,100 1,268 12,680 0.0 0 38,780 20.6 22,676 0 A12-4 97 0 291 0 291 17,460 0 0.0 0 17,460 11.3 12,418 0A132652795479947,940 0 2.4 6,414 47,940 47.1 51,767 0 A14 66 0 198 0 198 11,880 0 0.0 0 11,880 19.9 21,872 0 A15 128 0 384 0 384 23,040 0 0.0 0 23,040 131.8 144,973 0 A16 98 13 294 26 320 19,200 0 0.0 0 19,200 28.9 31,747 0 A16-1 163 0 489 0 489 29,340 0 0.0 0 29,340 18.9 20,777 0A177882341625015,000 0 0.6 1,620 15,000 32.5 35,804 0 A18 205 0 615 0 615 36,900 0 0.0 0 36,900 43.9 48,261 0 A18-1 6 0 18 0 18 1,080 0 0.0 0 1,080 2.4 2,609 0 A18-2 101 0 303 0 303 18,180 0 0.0 0 18,180 18.4 20,231 0 A18-3 50 0 150 0 150 9,000 0 0.0 0 9,000 8.0 8,844 0A192280684068441,040 511 5,110 0.0 0 46,150 63.4 69,762 0 A2 18 155 54 310 364 21,840 920 9,200 1.0 2,802 31,040 32.7 36,021 0 A20 261 2 783 4 787 47,220 0 0.0 0 47,220 57.5 63,214 0 A21 86 0 258 0 258 15,480 0 56.5 152,601 15,480 83.3 91,617 0 A22 167 0 501 0 501 30,060 0 1.7 4,692 30,060 34.4 37,869 0A23167315016256333,780 0 0.5 1,409 33,780 35.0 38,451 0 A24 263 34 789 68 857 51,420 0 0.0 0 51,420 5.3 5,785 0 A24-1 2 0 6 0 6 360 0 1.0 2,626 360 6.7 7,401 0 A24-2 0 0 0 0 0 0 0 0.0 0 0 0 0 A24-3 0 0 0 0 0 0 0 0.0 0 0 0 0A24-4 63 180 189 360 549 32,940 0 18.0 48,579 32,940 14.8 16,225 0 A24-5 2 0 6 0 6 360 0 0.0 0 360 2.3 2,537 0 A25 2 0 6 0 6 360 0 0.0 0 360 6.7 7,319 0 A25-1 2 0 6 0 6 360 0 0.0 0 360 20.4 22,397 0 A26 18 0 54 0 54 3,240 0 8.5 22,950 3,240 14.8 16,306 34,962 National Food CorpA275015015900031.7 85,653 900 43.0 47,249 A28 138 0 414 0 414 24,840 0 0.0 0 24,840 31.7 34,874 0 A4 83 57 249 114 363 21,780 0 0.7 1,986 21,780 15.7 17,317 0 A5 61 155 183 310 493 29,580 0 0.5 1,270 29,580 20.1 22,136 0 A6 202 330 606 660 1,266 75,960 0 2.2 5,904 75,960 64.0 70,420 0A7864258826615,960 603 6,030 0.2 540 21,990 30.2 33,194 0 A8 77 6 231 12 243 14,580 0 3.4 9,101 14,580 21.5 23,636 0 A9 61 0 183 0 183 10,980 0 8.4 22,809 10,980 25.3 27,831 0 B1 105 75 315 150 465 27,900 0 7.5 20,349 27,900 34.9 38,372 0 B2 0 0 0 0 0 0 0 0.0 0 0 0 0B35271561417010,200 0 6.5 17,668 10,200 15.9 17,520 0 B4 19 0 57 0 57 3,420 0 0.0 0 3,420 2.2 2,384 0 B5 12 0 36 0 36 2,160 0 0.0 0 2,160 2.0 2,198 0 CE1 42 4 126 8 134 8,040 0 0.0 0 8,040 10.1 11,147 0 CE2 66 26 198 52 250 15,000 0 0.2 540 15,000 14.4 15,847 0CE3940282028216,920 0 0.0 0 16,920 22.0 24,243 0 CE4 62 0 186 0 186 11,160 0 0.0 0 11,160 15.5 17,075 0 CE5 43 0 129 0 129 7,740 953 9,530 0.0 0 17,270 38.2 42,070 0 CE5-1 72 0 216 0 216 12,960 654 6,540 0.0 0 19,500 33.1 36,447 0 CE5-2 0 130 0 260 260 15,600 0 99.4 268,325 15,600 106.9 117,570 0CE5-3 228 6 684 12 696 41,760 0 0.0 0 41,760 52.3 57,485 0 CE5-4 38 0 114 0 114 6,840 0 3.1 8,424 6,840 13.9 15,237 0 CE5-5 27 28 81 56 137 8,220 0 0.0 0 8,220 10.0 10,994 0 CE5-6 78 0 234 0 234 14,040 0 0.0 0 14,040 15.6 17,205 0 CE5-7 433 0 1,299 0 1,299 77,940 1,611 16,110 14.1 38,189 94,050 104.2 114,648 0CE61520456045627,360 0 0.0 0 27,360 32.2 35,437 0 CE7 258 0 774 0 774 46,440 0 0.0 0 46,440 44.4 48,849 0 CE8 124 0 372 0 372 22,320 0 0.0 0 22,320 20.0 21,991 0 CE9 115 0 345 0 345 20,700 0 0.0 0 20,700 20.6 22,691 0 CW1 283 189 849 378 1,227 73,620 0 48.0 129,557 73,620 107.4 118,138 0CW101242372437622,560 0 1.7 4,596 22,560 28.4 31,227 Inflitration / Inflow Fixed or Pumped Flow (gpd) Total Residential/ School Flow (gpd) Residential Schools Commercial/ M:\Marysville\11447\Modeling\Flows\Node input 2011 for modela 2700 gpad.xls 1 of 3 Marysville 2011 Sewer Sub-Basin Flows BASINS (service area) Sewered Single Family Units Sewered Multi Family Units Single Family Population on Sewer Multi-Family Population on Sewer Total Existing Population On Sewer Residential Wastewater Flow (gpd) School Population School Wastewater Flow (gpd) Area (acres) Average Flow (gpd) Area (acres) Peak I/I Flow (gpd)Remark Inflitration / Inflow Fixed or Pumped Flow (gpd) Total Residential/ School Flow (gpd) Residential Schools Commercial/ CW11 14 0 42 0 42 2,520 0 15.6 42,131 2,520 19.7 21,689 16,367 Holiday Inn Exp (8263),Haggen (8104) CW11-1 35 0 105 0 105 6,300 0 28.1 75,863 6,300 35.7 39,316 CW12 41 3 123 6 129 7,740 0 18.6 50,242 7,740 31.0 34,152 0 CW13 35 95 105 190 295 17,700 0 33.3 89,933 17,700 43.2 47,496 8,512 Fred Meyer CW14 45 28 135 56 191 11,460 0 17.4 46,903 11,460 23.4 25,734 0CW15201602623,720 0 3.8 10,269 3,720 9.0 9,846 0 CW2 144 31 432 62 494 29,640 0 10.6 28,580 29,640 32.7 35,967 0 CW3 241 100 723 200 923 55,380 1,304 13,040 9.0 24,360 68,420 76.8 84,494 10,677 Marysville Care Center CW4 36 126 108 252 360 21,600 0 30.1 81,262 21,600 39.5 43,489 CW5 2 6 6 12 18 1,080 0 25.5 68,860 1,080 26.4 29,093 10,548 Captain Dizzy Car WashCW6242827256463638,160 0 3.1 8,385 38,160 25.2 27,678 0 CW7 79 37 237 74 311 18,660 274 2,740 34.1 92,138 21,400 55.5 61,093 0 CW8 120 160 360 320 680 40,800 0 24.4 65,760 40,800 44.4 48,790 0 CW9 1 0 3 0 3 180 0 15.4 41,588 180 31.2 34,373 0 D1 24 10 72 20 92 5,520 0 4.1 11,070 5,520 21.1 23,164 0D10960288028817,280 0 0.0 0 17,280 20.9 23,012 0 D10-1 0 0 0 0 0 0 0 0.0 0 0 0 0 D10-2 130 0 390 0 390 23,400 0 0.0 0 23,400 23.8 26,186 0 D10-3 0 0 0 0 0 0 0 0.0 0 0 0 0 D10-4 0 0 0 0 0 0 0 0.0 0 0 0 0D10-5 0 0 0 0 0 0 0 0.0 0 0 0 0 D10-6 167 0 501 0 501 30,060 0 0.0 0 30,060 26.5 29,181 0 D11 73 0 219 0 219 13,140 0 0.0 0 13,140 27.1 29,791 0 D12 226 0 678 0 678 40,680 0 0.0 0 40,680 60.5 66,585 0 D2 50 0 150 0 150 9,000 0 0.0 0 9,000 9.7 10,628 0D3850255025515,300 0 5.7 15,347 15,300 28.5 31,384 0 D3-1 137 3 411 6 417 25,020 0 0.0 0 25,020 43.4 47,729 0 D3-10 250 8 750 16 766 45,960 0 0.0 0 45,960 48.5 53,401 0 D3-11 414 0 1,242 0 1,242 74,520 0 0.0 0 74,520 71.0 78,150 0 D3-12 388 2 1,164 4 1,168 70,080 0 0.0 0 70,080 92.5 101,765 0D3-13 50 0 150 0 150 9,000 0 0.0 0 9,000 19.3 21,275 0 D3-2 133 0 399 0 399 23,940 0 0.0 0 23,940 19.7 21,644 0 D3-3 111 0 333 0 333 19,980 0 0.0 0 19,980 25.4 27,895 0 D3-4 81 4 243 8 251 15,060 607 6,070 0.0 0 21,130 17.1 18,851 0 D3-5 523 1 1,569 2 1,571 94,260 658 6,580 3.5 9,409 100,840 103.5 113,825 0D3-6 41 1 123 2 125 7,500 0 0.0 0 7,500 17.6 19,385 0 D3-7 127 0 381 0 381 22,860 0 0.0 0 22,860 21.4 23,542 0 D3-8 460 0 1,380 0 1,380 82,800 0 0.0 0 82,800 60.1 66,141 0 D3-9 252 0 756 0 756 45,360 0 0.0 0 45,360 54.3 59,763 0 D4 140 1 420 2 422 25,320 0 0.0 0 25,320 27.0 29,728 0D51830549054932,940 0 3.3 8,910 32,940 39.4 43,341 0 D5-1 0 0 0 0 0 0 618 6,180 6.1 16,401 6,180 17.0 18,718 9,337 YMCA D5-2 181 203 543 406 949 56,940 0 6.1 16,585 56,940 56.9 62,586 0 D6 211 0 633 0 633 37,980 0 0.0 0 37,980 50.7 55,809 0 D6-1 88 0 264 0 264 15,840 0 0.0 0 15,840 19.5 21,458 0D6-2 752 0 2,256 0 2,256 135,360 0 3.2 8,631 135,360 155.6 171,187 0 D6-3 97 2 291 4 295 17,700 0 0.0 0 17,700 28.2 30,989 0 D6-4 157 0 471 0 471 28,260 0 0.0 0 28,260 29.9 32,903 0 D6-5 263 0 789 0 789 47,340 0 0.0 0 47,340 40.3 44,283 0 D7 49 0 147 0 147 8,820 0 0.0 0 8,820 16.3 17,934 0D7-1 133 0 399 0 399 23,940 0 0.0 0 23,940 11.8 13,005 0 D7-2 146 0 438 0 438 26,280 0 0.0 0 26,280 20.2 22,180 0 D8 52 0 156 0 156 9,360 0 2.8 7,493 9,360 20.2 22,267 0 D9 145 0 435 0 435 26,100 0 0.0 0 26,100 42.9 47,186 D9-1 122 0 366 0 366 21,960 0 0.0 0 21,960 22.6 24,828F170210211,260 0 0.0 0 1,260 2.4 2,587 0 F10 0 0 0 0 0 0 0 50.6 136,704 0 48.5 53,396 0 F11 1 0 3 0 3 180 0 23.3 62,854 180 23.9 26,337 0 F12 4 0 12 0 12 720 0 50.8 137,065 720 50.2 55,175 F13 1 0 3 0 3 180 0 35.9 96,926 180 41.2 45,367 0F13-1 0 0 0 0 0 0 0 1.0 2,700 0 43.6 47,962 0 F13-2 36 0 108 0 108 6,480 0 0.0 0 6,480 19.3 21,184 0 F14 11 0 33 0 33 1,980 0 35.1 94,683 1,980 42.5 46,779 78,093 Pacific Coast Feather M:\Marysville\11447\Modeling\Flows\Node input 2011 for modela 2700 gpad.xls 2 of 3 Marysville 2011 Sewer Sub-Basin Flows BASINS (service area) Sewered Single Family Units Sewered Multi Family Units Single Family Population on Sewer Multi-Family Population on Sewer Total Existing Population On Sewer Residential Wastewater Flow (gpd) School Population School Wastewater Flow (gpd) Area (acres) Average Flow (gpd) Area (acres) Peak I/I Flow (gpd)Remark Inflitration / Inflow Fixed or Pumped Flow (gpd) Total Residential/ School Flow (gpd) Residential Schools Commercial/ F15 83 0 249 0 249 14,940 0 34.1 92,148 14,940 44.9 49,429 0F1624681484009.2 24,736 840 24.5 26,930 0 F17 4 0 12 0 12 720 0 20.9 56,306 720 21.5 23,694 F18 0 0 0 0 0 0 0 26.3 70,935 0 54.3 59,719 0 F19 0 0 0 0 0 0 0 48.5 130,954 0 48.6 53,495 8,419 Medallion Hotel F2 13 0 39 0 39 2,340 0 0.0 0 2,340 3.0 3,306 0F20160424808456433,840 0 52.7 142,361 33,840 74.6 82,051 0 F21 249 293 747 586 1,333 79,980 0 1.8 4,831 79,980 46.0 50,587 0 F22 26 75 78 150 228 13,680 0 30.4 82,109 13,680 47.1 51,827 0 F22-1 0 0 0 0 0 0 304 3,040 2.5 6,750 3,040 87.2 95,918 0 F3 69 18 207 36 243 14,580 0 0.0 0 14,580 32.3 35,504 0F42400720072043,200 0 0.0 0 43,200 50.8 55,848 0 F5 22 58 66 116 182 10,920 434 4,340 18.5 50,082 15,260 38.7 42,581 0 F6 45 0 135 0 135 8,100 0 0.0 0 8,100 9.1 10,059 0 F7 21 0 63 0 63 3,780 0 15.1 40,732 3,780 22.4 24,668 0 F8 5 6 15 12 27 1,620 0 9.5 25,650 1,620 14.6 16,032 0 F9 0 0 0 0 0 0 0 19.0 51,300 0 19.3 21,252 7,660 Northwest Composites G1 93 93 279 186 465 27,900 0 31.4 84,897 27,900 64.8 71,310 0 G2 121 104 363 208 571 34,260 0 6.4 17,306 34,260 42.2 46,468 0 G3 1 0 3 0 3 180 0 76.9 207,602 180 48.4 53,186 0 G4 0 0 0 0 0 0 0 22.5 60,698 0 22.4 24,637 0 G5 144 0 432 0 432 25,920 0 0.0 0 25,920 29.0 31,925 0 G6 130 0 390 0 390 23,400 0 0.0 0 23,400 24.8 27,320 0 G7 3 0 9 0 9 540 1,126 11,260 0.0 0 11,800 7.0 7,689 0 G8 0 0 0 0 0 0 0 10.5 28,381 0 10.5 11,563 0 Totals:15,569 3,248 46,707 6,496 53,203 3,192,180 12,471 124,710 1,269 3,425,707 3,316,890 4,979 5,476,950 184,575 Unit Person 60 Student/Staff 10 Commercial 2,700 Industrial 2,700 Peak I/I 1,100 Single Family 3.0 Multi Family 2.0 gpd/acre people/residence people/residence Unit Flow Rate gpd/person gpd/stud. of staff gpd/acre Unit Flow Table gpd/acre Population Table Sewered Population Total Population UGA Sewered Population UGA Population Non-UGA Population Non-UGA Sewered Population Total Sewered Population M:\Marysville\11447\Modeling\Flows\Node input 2011 for modela 2700 gpad.xls 3 of 3 Marysville 2017Sewer Sub-Basin FlowsBASINS (service area)Total Existing Population On SewerResidential Wastewater Flow (gpd)School PopulationSchool Wastewater Flow (gpd)Area (acres)Commercial Flow (gpd)2017 Area (acres)Peak I/I Flow (gpd)RemarkA1183011.1 30,0348312.9 10,332 0A1076645,9637297,2860.0053,24953.642,8730A1142125,23603.18,23925,23619.415,5440A1269341,59200.0041,59238.030,3880A12-137022,17600.0022,17623.218,5570A12-295057,02000.0057,02036.929,5380A12-344126,4601,47614,7580.0041,21824.019,1940A12-435121,07200.0021,07213.110,5110A1386551,91802.46,41451,91854.843,8170A1422113,23000.0013,23023.118,5130A1545127,06600.0027,066108.086,4300A1646327,77308.422,80127,77333.626,8720A16-172643,58200.0043,58222.017,5870A1738122,88500.61,62022,88537.930,3060A1868741,23800.0041,23851.140,8500A18-11639,77300.009,7732.82,2080A18-230318,18000.0018,18021.417,1240A18-319811,89400.0011,8949.47,4860A1992655,5845955,9470.0061,53173.859,0490A239023,3881,07110,7071.02,80234,09537.029,5700A2096557,87600.0057,87666.953,5060A2127016,218091.5247,10116,21896.977,5480A2271743,00101.74,69243,00140.132,0530A2366439,816016.544,60939,81640.732,5460A2494156,46000.0056,4606.14,8970A24-17414069.0186,2264147.86,2640A24-200080.0216,00000.000A24-300072.0194,40000.000A24-455133,030043.0116,07933,03017.213,7340A24-5105760100.0270,0005762.72,1480A258468090.0243,0004687.76,1950A25-174140195.0526,50041423.718,9580A26563,348078.5211,9503,34817.313,80240,690National Food CorpA27181,062062.1167,7821,06250.039,9930A2855333,17400.0033,17436.929,5190A441524,87000.71,98624,87018.314,6580A557334,36200.51,27034,36223.418,7370A61,697101,79003.28,604101,79074.559,6060A744226,5077027,0180.254033,52535.128,0960A834420,66403.49,10120,66425.020,0070A924114,44908.422,80914,44929.423,5570B176245,70209.926,70745,70240.632,4800B21669,93600.009,9360.000B327616,54706.517,66816,54718.514,8300B41508,99000.008,9902.52,0180B51297,75200.007,7522.31,8600CE118310,99200.0010,99211.89,4350CE237022,18200.254022,18216.813,4140CE333920,34000.0020,34025.720,5200CE421913,12200.0013,12218.114,4530CE520011,9701,10911,0910.0023,06144.535,6090CE5-125315,1677617,6120.0022,77938.630,8500CE5-226015,600099.4268,32515,600112.089,6010CE5-372543,52400.0043,52460.848,6570CE5-41146,84007.018,9466,84016.112,8970CE5-51619,65000.009,65011.69,3050CE5-623714,22000.0014,22018.214,5630CE5-71,58695,1351,87518,75054.1146,189113,885121.397,0420CE654032,38200.0032,38237.529,9950CE779147,43000.0047,43051.741,3480CE837222,32000.0022,32023.318,6140CE934820,86201.02,70020,86224.019,2060Inflitration / Inflow2017 Fixed or Pumped Flow (gpd)SchoolsCommercial/ IndustrialTotal Residential/ School Flow (gpd)ResidentialM:\Marysville\11447\Modeling\Flows\Node input 2017 for modela 2700 gpad.xls1 of 3 Marysville 2017Sewer Sub-Basin FlowsBASINS (service area)Total Existing Population On SewerResidential Wastewater Flow (gpd)School PopulationSchool Wastewater Flow (gpd)Area (acres)Commercial Flow (gpd)2017 Area (acres)Peak I/I Flow (gpd)RemarkInflitration / Inflow2017 Fixed or Pumped Flow (gpd)SchoolsCommercial/ IndustrialTotal Residential/ School Flow (gpd)ResidentialCW11,50190,080048.0129,55790,080125.099,9960CW1051931,12805.113,69131,12833.026,4320CW1118811,282015.6 42,13111,28222.9 18,358 19,049Holiday Inn Exp (8263), Haggen (8104)CW11-1 60536,304028.175,86336,30441.633,2790CW121669,936023.964,5179,93636.128,9070CW1331518,888033.389,93318,88850.340,2039,907Fred MeyerCW1430218,125017.446,90318,12527.221,7820CW1583149,88909.625,93449,88910.48,3340CW249529,694011.932,09029,69438.130,4440CW31,07664,5371,51815,1779.024,36079,71489.471,51812,426Marysville Care CenterCW443826,308034.392,53926,30846.036,8110CW5191,134025.869,7501,13430.824,62512,276Captain Dizzy Car WashCW677146,27703.710,00546,27729.323,4280CW731418,8223193,18946.7126,05822,01164.651,7110CW873644,172025.568,73044,17251.641,2980CW93180024.566,20218035.928,7340D11086,45604.111,0706,45624.519,6070D1028817,28000.0017,28024.319,4780D10-1724,342023.062,0824,3420.000D10-249829,863066.0178,20029,86327.722,1650D10-31227,33800.007,3380.000D10-41197,11600.007,1160.000D10-51005,988011.029,7005,9880.000D10-685351,19800.0051,19830.924,7000D1121913,14000.0013,14031.525,2160D1272943,74000.0043,74070.456,3600D21669,95400.009,95411.28,9960D330218,14105.715,34718,14133.226,5640D3-149529,68200.0029,68250.540,4000D3-1090154,07500.0054,07556.545,2000D3-111,37782,63800.0082,63882.766,1480D3-121,45887,49000.0087,490107.786,1370D3-1323213,89800.0013,89822.518,0080D3-240924,53400.0024,53422.918,3200D3-339723,83800.0023,83829.523,6120D3-431418,8637067,0650.0025,92819.915,9560D3-51,909114,5197667,6583.59,409122,177120.496,3450D3-617010,20401.54,05010,20420.516,4080D3-746327,77400.0027,77424.919,9270D3-81,38282,90800.0082,90870.055,9840D3-987952,72200.0052,72263.250,5860D442425,41000.0025,41031.525,1620D556533,89403.38,91033,89445.936,6850D5-1007197,1936.116,4017,19319.815,84410,867YMCAD5-296157,64206.116,58557,64266.252,9750D667540,48200.0040,48259.047,2390D6-127116,25400.0016,25422.718,1630D6-22,510150,60603.28,631150,606181.1144,8990D6-330218,11400.0018,11432.826,2300D6-447228,31400.0028,31434.827,8500D6-592855,681020.054,00055,68146.937,4820D71519,03600.009,03619.015,1800D7-139923,94000.0023,94013.811,0070D7-243826,28000.0026,28023.518,7740D81619,64802.87,4939,64823.618,8470D947728,60200.0028,60249.939,9400D9-142925,72500.0025,72526.321,0160F1513,05300.003,0532.72,1900F10154078.1210,9515456.545,1960F113180029.379,05418027.922,2920F12148280106.5287,56482858.446,7020M:\Marysville\11447\Modeling\Flows\Node input 2017 for modela 2700 gpad.xls2 of 3 Marysville 2017Sewer Sub-Basin FlowsBASINS (service area)Total Existing Population On SewerResidential Wastewater Flow (gpd)School PopulationSchool Wastewater Flow (gpd)Area (acres)Commercial Flow (gpd)2017 Area (acres)Peak I/I Flow (gpd)RemarkInflitration / Inflow2017 Fixed or Pumped Flow (gpd)SchoolsCommercial/ IndustrialTotal Residential/ School Flow (gpd)ResidentialF133180070.9191,42618048.038,4000F13-142500121.0326,70025050.740,5960F13-21307,792066.0178,2007,79222.417,9310F14492,952085.1229,6832,95249.539,59690,888Pacific Coast FeatherF1525315,156064.1173,19215,15652.341,8380F1614840051.0137,63284028.522,7940F17201,206040.9110,3061,20625.120,0560F1800038.3103,335039.631,6990F1900048.5130,954052.542,0169,798Medallion HotelF21388,28000.008,2803.52,7980F2065839,468074.7201,76139,46886.869,4500F211,56393,753019.853,43193,75353.542,8190F2246828,062030.482,10928,06254.843,8690F22-1613,6743543,538105.3284,2237,212101.581,1880F324314,58000.0014,58037.630,0510F478647,14200.0047,14259.147,2720F525115,0475055,05123.563,58220,09845.136,0420F61358,10000.008,10010.68,5150F7895,318029.178,5325,31826.120,8800F8382,303018.5 49,9502,30317.0 13,570 0F900031.0 83,700022.5 17,989 8,915 Northwest CompositesG155032,972037.0 99,99632,97275.4 60,360 0G273544,104011.4 30,80644,10449.2 39,332 0G33180076.9 207,60218056.3 45,019 0G49540027.5 74,19854026.1 20,854 0G543225,92000.0025,92033.8 27,023 0G639023,40000.0023,40028.9 23,124 0G7985,889 1,310 13,105 28.8 77,76418,9938.1 6,508 0G814835010.5 28,38183512.2 9,787 0Totals:65,0243,901,41714,514145,1432,9638,000,8084,046,5605,7084,566,294214,817Population TableUnitPerson60Student/Staff10Commercial 2,700 Industrial 2,700 Peak I/I800Single Family3.0Sewered PopulationMulti Family2.0gpd/acregpd/acrepeople/residencepeople/residenceUnit Flow Tablegpd/acreUnit Flow Rategpd/persongpd/stud. of staffUGA Sewered Population 59,656Non-UGA Sewered Population 2,594Total Sewered Population 62,250Total Population72,616UGA Population 69,338Non-UGA Population 3,278M:\Marysville\11447\Modeling\Flows\Node input 2017 for modela 2700 gpad.xls3 of 3 Marysville 2031Sewer Sub-Basin FlowsBASINS (service area)Total Existing Population On SewerResidential Wastewater Flow (gpd)School PopulationSchool Wastewater Flow (gpd)Area (acres)Average Flow (gpd)2031 Area (acres)Peak I/I Flow (gpd)RemarkA1231,400011.1 30,0341,40017.2 13,726 0A1090053,9799689,6790.0063,65871.256,9560A1145327,18903.18,23927,18925.820,6510A1280948,56400.0048,56450.540,3700A12-135921,54600.0021,54630.824,6530A12-294656,77200.0056,77249.139,2420A12-341925,1371,96119,6050.0044,74231.925,4990A12-442225,30800.0025,30817.513,9640A1385651,35702.46,41451,35772.858,2110A1425915,56100.0015,56130.724,5940A1557734,63600.0034,636108.086,4300A1668040,81208.422,80140,81244.635,6990A16-11,02361,38900.0061,38929.223,3640A1752331,35000.61,62031,35050.340,2610A1866740,01400.0040,01467.854,2680A18-141624,96600.0024,9663.72,9330A18-228817,27100.0017,27125.320,2020A18-334220,53400.0020,53412.49,9450A191,27176,2667907,9010.0084,16798.178,4450A237422,4581,42214,2251.02,80236,68337.029,5700A201,06463,84000.0063,84088.971,0830A2127116,245091.5247,10116,245128.8103,0220A2287852,66801.74,69252,66853.242,5820A231,00260,144016.544,60960,14454.043,2370A2489453,63700.0053,6378.16,5060A24-19513069.0186,22651310.48,3220A24-200080.0216,00000.000A24-300072.0194,40000.000A24-452631,578043.0116,07931,57822.818,2450A24-5171,0260100.0270,0001,0263.62,8530A2511684090.0243,00068410.38,2310A25-195130195.0526,50051331.525,1850A26573,420078.5211,9503,42022.918,33654,057National Food CorpA27231,368062.1167,7821,36866.453,1300A2872743,60500.0043,60549.039,2160A446427,81600.71,98627,81624.319,4730A565038,98800.51,27038,98831.124,8920A61,994119,64303.28,604119,64399.079,1850A766039,6159329,3230.254048,93846.737,3260A844626,73303.49,10126,73333.226,5780A928517,10008.422,80917,10035.828,6650B11,08264,92309.926,70764,92353.943,1490B243025,82100.0025,8210.000B346728,04406.517,66828,04424.619,7010B427616,58700.0016,5873.42,6810B536321,80800.0021,8083.12,4720CE123013,79400.0013,79415.712,5350CE253732,20500.254032,20522.317,8200CE338222,91400.0022,91434.127,2610CE423414,02200.0014,02224.019,2000CE531919,1521,47314,7350.0033,88759.147,3060CE5-126215,7321,01110,1120.0025,84451.240,9840CE5-224714,820099.4268,32514,820112.089,6010CE5-370142,06600.0042,06680.864,6410CE5-41086,49807.018,9466,49821.417,1340CE5-51629,69000.009,69015.512,3620CE5-622513,50900.0013,50924.219,3470CE5-72,949176,9152,49124,90954.1146,189201,824161.1128,9190CE661837,10700.0037,10749.839,8490CE776145,65700.0045,65768.654,8760CE835321,20400.0021,20427.321,8280CE933620,17801.02,70020,17831.925,5150CW11,57594,506048.0129,55794,506166.1132,8430CW1063738,19005.113,69138,19043.935,11402031 Fixed or Pumped Flow (gpd)ResidentialSchoolsCommercial/ Total Residential/ School Flow (gpd)Inflitration / InflowM:\Marysville\11447\Modeling\Flows\Node input 2031 for modela 2700 gpad Aug.xls1 of 3 Marysville 2031Sewer Sub-Basin FlowsBASINS (service area)Total Existing Population On SewerResidential Wastewater Flow (gpd)School PopulationSchool Wastewater Flow (gpd)Area (acres)Average Flow (gpd)2031 Area (acres)Peak I/I Flow (gpd)Remark2031 Fixed or Pumped Flow (gpd)ResidentialSchoolsCommercial/ Total Residential/ School Flow (gpd)Inflitration / InflowCW1150230,096015.6 42,13130,09630.5 24,389 25,306Holiday Inn Exp (8263), Haggen (8104)CW11-1 2,097125,838028.175,863125,83855.344,2100CW1222513,509023.964,51713,50948.038,4030CW1334320,577033.389,93320,57752.441,91913,161Fred MeyerCW1472043,212017.446,90343,21236.228,9380CW152,985179,07509.625,934179,07513.811,0720CW247228,329011.932,09028,32950.640,4440CW31,06063,6122,01620,1629.024,36083,774101.681,29216,508Marysville Care CenterCW447628,557034.392,53928,55761.148,9020CW5201,197025.869,7501,19733.626,91616,309Captain Dizzy Car WashCW683349,98903.710,00549,98938.931,1240CW730418,2404244,23646.7126,05822,47676.461,0850CW873544,118025.568,73044,11868.654,8630CW93171024.566,20217135.928,7340D11307,80904.111,0707,80932.626,0480D1027416,41600.0016,41632.325,8770D10-179147,487023.062,08247,4870.000D10-21,59195,473066.0178,20095,47336.829,4460D10-386852,05600.0052,0560.000D10-471242,74400.0042,7440.000D10-529517,712011.029,70017,7120.000D10-61,48889,27900.0089,27941.032,8140D1120812,48300.0012,48334.127,2670D1269341,55300.0041,55388.871,0360D21609,57600.009,57614.911,9510D331618,98105.715,34718,98144.135,2900D3-155333,17400.0033,17467.153,6700D3-1088453,06700.0053,06775.160,0480D3-111,34280,54100.0080,541109.887,8780D3-122,294137,66900.00137,669143.0114,4320D3-1353131,86000.0031,86029.923,9230D3-239023,42700.0023,42730.424,3390D3-343025,82100.0025,82139.231,3680D3-451330,7919399,3850.0040,17626.521,1980D3-52,503150,1951,01710,1743.59,409160,369160.0127,9940D3-636822,07501.54,05022,07527.221,7980D3-751030,60900.0030,60933.126,4720D3-81,31779,00200.0079,00293.074,3740D3-984150,44500.0050,44579.863,8110D440624,33900.0024,33938.931,1260D555933,51603.38,91033,51659.247,3610D5-1009569,5556.116,4019,55526.321,04814,436YMCAD5-291955,11906.116,58555,11978.562,7890D664738,81700.0038,81776.361,0590D6-125915,56100.0015,56126.821,4670D6-22,423145,35003.28,631145,350240.6192,4970D6-328917,32800.0017,32837.930,3450D6-445027,01800.0027,01846.236,9980D6-51,38983,326020.054,00083,32662.249,7950D71519,06300.009,06323.518,8240D7-137922,74300.0022,74318.314,6230D7-241624,96600.0024,96631.224,9410D81579,40502.87,4939,40528.422,6920D945927,53100.0027,53166.353,0600D9-142225,30800.0025,30834.927,9190F11307,77900.007,7793.62,9090F103171078.1210,95117175.160,0420F113171029.379,05417137.029,6150F12171,0260106.5287,5641,02677.662,0440F133171070.9191,42617163.851,0140F13-141324,7930121.0326,70024,79367.453,9320F13-21549,234066.0178,2009,23429.823,8210F14834,959085.1229,6834,95965.852,602120,744Pacific Coast FeatherM:\Marysville\11447\Modeling\Flows\Node input 2031 for modela 2700 gpad Aug.xls2 of 3 Marysville 2031Sewer Sub-Basin FlowsBASINS (service area)Total Existing Population On SewerResidential Wastewater Flow (gpd)School PopulationSchool Wastewater Flow (gpd)Area (acres)Average Flow (gpd)2031 Area (acres)Peak I/I Flow (gpd)Remark2031 Fixed or Pumped Flow (gpd)ResidentialSchoolsCommercial/ Total Residential/ School Flow (gpd)Inflitration / InflowF1524814,877064.1173,19214,87769.555,5820F1613798051.0137,63279837.930,2820F17372,223040.9110,3062,22333.326,6440F1800038.3103,335039.631,6990F1900048.5130,954052.542,01613,017Medallion HotelF235121,03300.0021,0334.63,7180F201,08865,270074.7201,76165,270115.392,2640F211,745104,709019.853,431104,70971.156,8840F2285651,357030.482,10951,35772.858,2790F22-11,14668,7534704,700105.3284,22373,454134.8107,8580F323113,85100.0013,85139.231,3410F489253,52300.0053,52378.562,8000F556233,7036716,71023.563,58240,41359.947,8820F61287,69500.007,69513.210,5790F721312,808029.178,53212,80834.727,7390F81358,102018.5 49,9508,10222.5 18,028 0F900031.0 83,700029.9 23,898 11,844 Northwest CompositesG170942,567037.0 99,99642,567100.2 80,187 0G21,40684,359011.4 30,80684,35965.3 52,253 0G33171076.9 207,60217174.8 59,807 0G4291,710027.5 74,1981,71034.6 27,704 0G541024,62400.0 024,62444.9 35,899 0G637122,23000.0 022,23038.4 30,720 0G733520,111 1,741 17,410 28.8 77,76437,52110.8 8,646 0G8663,975010.5 28,3813,97516.3 13,002 0Totals:86,7325,203,89519,282192,8222,9638,000,8085,396,7177,3405,871,741285,382 19,554,649 5.405.870.2919.55Population Table6010Commercial 2,700 1,000 8003.0Sewered Population2.0Unit Flow Rategpd/persongpd/stud. of staffpeople/residencepeople/residenceUnit Flow Tablegpd/acreStudent/StaffIndustrialgpd/acrePeak I/Igpd/acreSingle FamilyMulti FamilyTotal Population84,989UGA Population 87,757Non-UGA Population 3,278UnitPerson84,989Non-UGA Sewered Population 3,278Total Sewered Population 87,757UGA Sewered PopulationM:\Marysville\11447\Modeling\Flows\Node input 2031 for modela 2700 gpad Aug.xls3 of 3 Marysville 2031 Sewer Sub-Basin Flows BASINS (service area) Total Existing Population On Sewer Residential Wastewater Flow (gpd) School Population School Wastewater Flow (gpd) Area (acres) Average Flow (gpd) 2031 Area (acres) Peak I/I Flow (gpd)Remark A1 23 1,400 0 11.1 30,034 1,400 17.2 13,726 0 A10 900 53,979 968 9,679 0.0 0 63,658 71.2 56,956 0 A11 453 27,189 0 3.1 8,239 27,189 25.8 20,651 0A1280948,564 0 0.0 0 48,564 50.5 40,370 0 A12-1 359 21,546 0 0.0 0 21,546 30.8 24,653 0 A12-2 946 56,772 0 0.0 0 56,772 49.1 39,242 0 A12-3 419 25,137 1,961 19,605 0.0 0 44,742 31.9 25,499 0 A12-4 422 25,308 0 0.0 0 25,308 17.5 13,964 0A1385651,357 0 2.4 6,414 51,357 72.8 58,211 0 A14 259 15,561 0 0.0 0 15,561 30.7 24,594 0 A15 577 34,636 0 0.0 0 34,636 108.0 86,430 0 A16 680 40,812 0 8.4 22,801 40,812 44.6 35,699 0 A16(Future)3,484 209,040 0 0.0 0 209,040 1182.0 945,600 0A16-1 1,023 61,389 0 0.0 0 61,389 29.2 23,364 0 A17 523 31,350 0 0.6 1,620 31,350 50.3 40,261 0 A18 667 40,014 0 0.0 0 40,014 67.8 54,268 0 A18(Future)531 31,860 0 0.0 0 31,860 180.0 144,000 0 A18-1 416 24,966 0 0.0 0 24,966 3.7 2,933 0A18-2 288 17,271 0 0.0 0 17,271 25.3 20,202 0 A18-3 342 20,534 0 0.0 0 20,534 12.4 9,945 0 A18-3(Future)473 28,380 0 0.0 0 28,380 160.0 128,000 0 A19 1,271 76,266 790 7,901 0.0 0 84,167 98.1 78,445 0 A2 374 22,458 1,422 14,225 1.0 2,802 36,683 37.0 29,570 0A201,064 63,840 0 0.0 0 63,840 88.9 71,083 0 A21 271 16,245 0 91.5 247,101 16,245 128.8 103,022 0 A22 878 52,668 0 1.7 4,692 52,668 53.2 42,582 0 A23 1,002 60,144 0 16.5 44,609 60,144 54.0 43,237 0 A24 894 53,637 0 0.0 0 53,637 8.1 6,506 0A24(Future)5,993 359,580 0 0.0 0 359,580 2034.0 1,627,200 0 A24-1 9 513 0 69.0 186,226 513 10.4 8,322 0 A24-2 0 0 0 80.0 216,000 0 0.0 0 0 A24-3 0 0 0 72.0 194,400 0 0.0 0 0 A24-4 526 31,578 0 43.0 116,079 31,578 22.8 18,245 0A24-5 17 1,026 0 100.0 270,000 1,026 3.6 2,853 0 A25 11 684 0 90.0 243,000 684 10.3 8,231 0 A25-1 9 513 0 195.0 526,500 513 31.5 25,185 0 A26 57 3,420 0 78.5 211,950 3,420 22.9 18,336 54,057 National Food Corp A27 23 1,368 0 62.1 167,782 1,368 66.4 53,130 0A2872743,605 0 0.0 0 43,605 49.0 39,216 0 A4 464 27,816 0 0.7 1,986 27,816 24.3 19,473 0 A5 650 38,988 0 0.5 1,270 38,988 31.1 24,892 0 A6 1,994 119,643 0 3.2 8,604 119,643 99.0 79,185 0 A7 660 39,615 932 9,323 0.2 540 48,938 46.7 37,326 0A844626,733 0 3.4 9,101 26,733 33.2 26,578 0 A9 285 17,100 0 8.4 22,809 17,100 35.8 28,665 0 B1 1,082 64,923 0 9.9 26,707 64,923 53.9 43,149 0 B2 430 25,821 0 0.0 0 25,821 0.0 0 0 B3 467 28,044 0 6.5 17,668 28,044 24.6 19,701 0B427616,587 0 0.0 0 16,587 3.4 2,681 0 B5 363 21,808 0 0.0 0 21,808 3.1 2,472 0 CE1 230 13,794 0 0.0 0 13,794 15.7 12,535 0 CE2 537 32,205 0 0.2 540 32,205 22.3 17,820 0 CE3 382 22,914 0 0.0 0 22,914 34.1 27,261 0CE423414,022 0 0.0 0 14,022 24.0 19,200 0 CE5 319 19,152 1,473 14,735 0.0 0 33,887 59.1 47,306 0 CE5-1 262 15,732 1,011 10,112 0.0 0 25,844 51.2 40,984 0 CE5-2 247 14,820 0 99.4 268,325 14,820 112.0 89,601 0 CE5-3 701 42,066 0 0.0 0 42,066 80.8 64,641 0CE5-3(Future)1,092 65,520 0 0.0 0 65,520 370.0 296,000 0 CE5-4 108 6,498 0 7.0 18,946 6,498 21.4 17,134 0 CE5-5 162 9,690 0 0.0 0 9,690 15.5 12,362 0 CE5-6 225 13,509 0 0.0 0 13,509 24.2 19,347 0 CE5-7 2,949 176,915 2,491 24,909 54.1 146,189 201,824 161.1 128,919 0CE661837,107 0 0.0 0 37,107 49.8 39,849 0 Inflitration / Inflow 2031 Fixed or Pumped Flow (gpd) Residential Schools Commercial/ Total Residential/ School Flow (gpd) M:\Marysville\11447\Modeling\Flows\Node input 2031 for modela 2700 gpad w planning areas Aug.xls 1 of 3 Marysville 2031 Sewer Sub-Basin Flows BASINS (service area) Total Existing Population On Sewer Residential Wastewater Flow (gpd) School Population School Wastewater Flow (gpd) Area (acres) Average Flow (gpd) 2031 Area (acres) Peak I/I Flow (gpd)Remark Inflitration / Inflow 2031 Fixed or Pumped Flow (gpd) Residential Schools Commercial/ Total Residential/ School Flow (gpd) CE7 761 45,657 0 0.0 0 45,657 68.6 54,876 0CE835321,204 0 0.0 0 21,204 27.3 21,828 0 CE9 336 20,178 0 1.0 2,700 20,178 31.9 25,515 0 CW1 1,575 94,506 0 48.0 129,557 94,506 166.1 132,843 0 CW10 637 38,190 0 5.1 13,691 38,190 43.9 35,114 0 CW11 502 30,096 0 15.6 42,131 30,096 30.5 24,389 25,306 Holiday Inn Exp (8263),Haggen (8104) CW11-1 2,097 125,838 0 28.1 75,863 125,838 55.3 44,210 0 CW12 225 13,509 0 23.9 64,517 13,509 48.0 38,403 0 CW13 343 20,577 0 33.3 89,933 20,577 52.4 41,919 13,161 Fred Meyer CW14 720 43,212 0 17.4 46,903 43,212 36.2 28,938 0CW152,985 179,075 0 9.6 25,934 179,075 13.8 11,072 0 CW2 472 28,329 0 11.9 32,090 28,329 50.6 40,444 0 CW3 1,060 63,612 2,016 20,162 9.0 24,360 83,774 101.6 81,292 16,508 Marysville Care Center CW4 476 28,557 0 34.3 92,539 28,557 61.1 48,902 0 CW5 20 1,197 0 25.8 69,750 1,197 33.6 26,916 16,309 Captain Dizzy Car WashCW683349,989 0 3.7 10,005 49,989 38.9 31,124 0 CW7 304 18,240 424 4,236 46.7 126,058 22,476 76.4 61,085 0 CW8 735 44,118 0 25.5 68,730 44,118 68.6 54,863 0 CW9 3 171 0 24.5 66,202 171 35.9 28,734 0 D1 130 7,809 0 4.1 11,070 7,809 32.6 26,048 0D1027416,416 0 0.0 0 16,416 32.3 25,877 0 D10-1 791 47,487 0 23.0 62,082 47,487 0.0 0 0 D10-2 1,591 95,473 0 66.0 178,200 95,473 36.8 29,446 0 D10-3 868 52,056 0 0.0 0 52,056 0.0 0 0 D10-4 712 42,744 0 0.0 0 42,744 0.0 0 0D10-5 295 17,712 0 11.0 29,700 17,712 0.0 0 0 D10-6 1,488 89,279 0 0.0 0 89,279 41.0 32,814 0 D11 208 12,483 0 0.0 0 12,483 34.1 27,267 0 D12 693 41,553 0 0.0 0 41,553 88.8 71,036 0 D2 160 9,576 0 0.0 0 9,576 14.9 11,951 0D331618,981 0 5.7 15,347 18,981 44.1 35,290 0 D3-1 553 33,174 0 0.0 0 33,174 67.1 53,670 0 D3-10 884 53,067 0 0.0 0 53,067 75.1 60,048 0 D3-11 1,342 80,541 0 0.0 0 80,541 109.8 87,878 0 D3-12 2,294 137,669 0 0.0 0 137,669 143.0 114,432 0D3-13 531 31,860 0 0.0 0 31,860 29.9 23,923 0 D3-2 390 23,427 0 0.0 0 23,427 30.4 24,339 0 D3-3 430 25,821 0 0.0 0 25,821 39.2 31,368 0 D3-4 513 30,791 939 9,385 0.0 0 40,176 26.5 21,198 0 D3-5 2,503 150,195 1,017 10,174 3.5 9,409 160,369 160.0 127,994 0D3-6 368 22,075 0 1.5 4,050 22,075 27.2 21,798 0 D3-7 510 30,609 0 0.0 0 30,609 33.1 26,472 0 D3-8 1,317 79,002 0 0.0 0 79,002 93.0 74,374 0 D3-9 841 50,445 0 0.0 0 50,445 79.8 63,811 0 D4 406 24,339 0 0.0 0 24,339 38.9 31,126 0D555933,516 0 3.3 8,910 33,516 59.2 47,361 0 D5-1 0 0 956 9,555 6.1 16,401 9,555 26.3 21,048 14,436 YMCA D5-2 919 55,119 0 6.1 16,585 55,119 78.5 62,789 0 D6 647 38,817 0 0.0 0 38,817 76.3 61,059 0 D6-1 259 15,561 0 0.0 0 15,561 26.8 21,467 0D6-2 2,423 145,350 0 3.2 8,631 145,350 240.6 192,497 0 D6-3 289 17,328 0 0.0 0 17,328 37.9 30,345 0 D6-4 450 27,018 0 0.0 0 27,018 46.2 36,998 0 D6-5 1,389 83,326 0 20.0 54,000 83,326 62.2 49,795 0 D7 151 9,063 0 0.0 0 9,063 23.5 18,824 0D7-1 379 22,743 0 0.0 0 22,743 18.3 14,623 0 D7-2 416 24,966 0 0.0 0 24,966 31.2 24,941 0 D8 157 9,405 0 2.8 7,493 9,405 28.4 22,692 0 D9 459 27,531 0 0.0 0 27,531 66.3 53,060 0 D9-1 422 25,308 0 0.0 0 25,308 34.9 27,919 0F11307,779 0 0.0 0 7,779 3.6 2,909 0 F10 3 171 0 78.1 210,951 171 75.1 60,042 0 F11 3 171 0 29.3 79,054 171 37.0 29,615 0 M:\Marysville\11447\Modeling\Flows\Node input 2031 for modela 2700 gpad w planning areas Aug.xls 2 of 3 Marysville 2031 Sewer Sub-Basin Flows BASINS (service area) Total Existing Population On Sewer Residential Wastewater Flow (gpd) School Population School Wastewater Flow (gpd) Area (acres) Average Flow (gpd) 2031 Area (acres) Peak I/I Flow (gpd)Remark Inflitration / Inflow 2031 Fixed or Pumped Flow (gpd) Residential Schools Commercial/ Total Residential/ School Flow (gpd) F12 17 1,026 0 106.5 287,564 1,026 77.6 62,044 0F133171070.9 191,426 171 63.8 51,014 0 F13(Future)28,405 1,704,300 0 0.0 0 1,704,300 2153.0 1,722,400 0 F13-1 413 24,793 0 121.0 326,700 24,793 67.4 53,932 0 F13-2 154 9,234 0 66.0 178,200 9,234 29.8 23,821 0 F14 83 4,959 0 85.1 229,683 4,959 65.8 52,602 120,744 Pacific Coast FeatherF1524814,877 0 64.1 173,192 14,877 69.5 55,582 0 F16 13 798 0 51.0 137,632 798 37.9 30,282 0 F17 37 2,223 0 40.9 110,306 2,223 33.3 26,644 0 F18 0 0 0 38.3 103,335 0 39.6 31,699 0 F19 0 0 0 48.5 130,954 0 52.5 42,016 13,017 Medallion HotelF235121,033 0 0.0 0 21,033 4.6 3,718 0 F20 1,088 65,270 0 74.7 201,761 65,270 115.3 92,264 0 F21 1,745 104,709 0 19.8 53,431 104,709 71.1 56,884 0 F22 856 51,357 0 30.4 82,109 51,357 72.8 58,279 0 F22(Future)28,291 1,697,460 0 0.0 0 1,697,460 2144.0 1,715,200 0F22-1 1,146 68,753 470 4,700 105.3 284,223 73,454 134.8 107,858 0 F3 231 13,851 0 0.0 0 13,851 39.2 31,341 0 F4 892 53,523 0 0.0 0 53,523 78.5 62,800 0 F5 562 33,703 671 6,710 23.5 63,582 40,413 59.9 47,882 0 F6 128 7,695 0 0.0 0 7,695 13.2 10,579 0F721312,808 0 29.1 78,532 12,808 34.7 27,739 0 F8 135 8,102 0 18.5 49,950 8,102 22.5 18,028 0 F9 0 0 0 31.0 83,700 0 29.9 23,898 11,844 Northwest Composites G1 709 42,567 0 37.0 99,996 42,567 100.2 80,187 0 G2 1,406 84,359 0 11.4 30,806 84,359 65.3 52,253 0 G3 3 171 0 76.9 207,602 171 74.8 59,807 0 G4 29 1,710 0 27.5 74,198 1,710 34.6 27,704 0 G5 410 24,624 0 0.0 0 24,624 44.9 35,899 0 G6 371 22,230 0 0.0 0 22,230 38.4 30,720 0 G7 335 20,111 1,741 17,410 28.8 77,764 37,521 10.8 8,646 0 G8 66 3,975 0 10.5 28,381 3,975 16.3 13,002 0 Totals:65,024 9,300,035 19,282 192,822 2,963 8,000,808 9,492,857 15,563 12,450,141 285,382 6010 Commercial 2,700 1,000800 3.0 2.0 gpd/acre people/residence people/residence Single Family Multi Family Peak I/IIndustrial Unit Flow Rate gpd/persongpd/stud. of staff gpd/acre Unit Flow Table Person gpd/acre Unit Student/Staff Population Table 159,575Total Planning Population 88,032UGA Population 71,543Non-UGA Population M:\Marysville\11447\Modeling\Flows\Node input 2031 for modela 2700 gpad w planning areas Aug.xls 3 of 3 Marysville Sewer Comprehensive Plan 2011 Model Input Sub-Basin Load 1: Residential Input1 (gpm) Load 2: Commercial Input (gpm) Load 3: I/I Input (gpm) Load 4: Fixed Flow (gpm) Input Node A1 0.0 20.9 8.5 0.0 S-MH-3559 A10 10.8 0.0 0.0 0.0 S-MH-2323 A10 9.4 0.0 17.6 0.0 S-MH-2141 A10 9.4 0.0 17.6 0.0 S-MH-2332 A11 15.0 5.7 12.8 0.0 S-MH-2189 A12 11.3 0.0 12.5 0.0 S-MH-2290 A12 11.3 0.0 12.5 0.0 S-MH-2198 A12-1 14.8 0.0 15.2 0.0 S-MH-2300 A12-2 33.4 0.0 24.2 0.0 S-MH-2225 A12-3 15.5 0.0 0.0 0.0 S-MH-3632 A12-3 5.9 0.0 7.9 0.0 S-MH-2259 A12-3 5.7 0.0 7.9 0.0 S-MH-2235 A12-4 12.1 0.0 8.6 0.0 MH-231 A13 23.5 2.2 24.0 0.0 S-MH-2315 A13 9.8 2.2 12.0 0.0 S-MH-3791 A14 8.3 0.0 15.2 0.0 S-MH-2386 A15 8.0 0.0 50.3 0.0 S-MH-2396 A15 8.0 0.0 50.3 0.0 S-MH-2419 A16 6.7 0.0 11.0 0.0 S-MH-2402 A16 6.7 0.0 11.0 0.0 S-MH-2401 A16-1 20.4 0.0 14.4 0.0 S-MH-4810 A16-1 20.4 0.0 14.4 0.0 S-MH-4742 A17 10.4 1.1 24.9 0.0 S-MH-2739 A18 9.9 0.0 13.6 0.0 S-MH-2743 A18 7.9 0.0 9.9 0.0 S-MH-2742 A18 7.9 0.0 9.9 0.0 S-MH-2856 A18-1 0.8 0.0 1.8 0.0 S-MH-2915 A18-2 12.6 0.0 14.0 0.0 S-MH-2865 A18-3 6.3 0.0 6.1 0.0 S-MH-2840 A19 32.0 0.0 48.4 0.0 S-MH-2733 A2 21.6 1.9 25.0 0.0 S-MH-336 A20 10.9 0.0 14.6 0.0 S-MH-2887 A20 10.9 0.0 14.6 0.0 MH-4 A20 10.9 0.0 14.6 0.0 S-MH-2727 A21 5.6 0.0 27.9 0.0 S-MH-2597 A21 2.7 53.0 14.0 0.0 S-MH-2980 A21 2.4 53.0 21.7 0.0 S-MH-2772 A22 8.7 0.0 8.8 0.0 S-MH-2795 A22 8.7 1.6 8.8 0.0 S-MH-2781 A22 3.6 1.6 8.8 0.0 S-MH-3595 A23 11.7 0.8 13.3 0.0 S-MH-2919 A23 11.7 0.2 13.4 0.0 S-MH-2969 A24 35.7 0.0 4.0 0.0 S-MH-3016 A24-1 0.1 0.9 2.6 0.0 S-MH-2815 A24-1 0.1 0.9 2.6 0.0 S-MH-3022 A24-2 0.0 0.0 0.0 0.0 S-MH-3614 A24-2 0.0 0.0 0.0 0.0 S-MH-3619 A24-3 0.0 0.0 0.0 0.0 S-MH-3622 A24-3 0.0 0.0 0.0 0.0 S-MH-3617 A24-4 7.6 0.0 3.8 0.0 S-MH-3080 A24-4 7.6 33.7 3.7 0.0 S-MH-3099 A24-4 7.6 0.0 3.7 0.0 S-MH-3077 A24-5 0.3 0.0 1.8 0.0 S-MH-2814 A25 0.3 0.0 5.1 0.0 S-MH-3837 A25-1 0.3 0.0 15.6 0.0 S-MH-3143 A26 0.9 4.0 3.8 24.3 S-MH-3422 A26 0.7 8.0 3.8 0.0 S-MH-3838 A26 0.7 4.0 3.8 0.0 S-MH-3139 A27 0.5 59.5 26.2 0.0 S-MH-3415 A27 0.1 0.0 6.6 0.0 S-MH-3403 A28 11.5 0.0 16.1 0.0 S-MH-3430 A28 5.8 0.0 8.1 0.0 S-MH-3443 A4 15.1 1.4 12.0 0.0 S-MH-357 A5 20.5 0.9 15.4 0.0 S-MH-277 A6 18.1 2.0 16.3 0.0 MH-22 A6 17.3 2.0 16.3 0.0 S-MH-3768 A6 17.3 0.0 16.3 0.0 S-MH-1548 A7 8.9 0.0 23.1 0.0 S-MH-1455 A7 6.4 0.4 0.0 0.0 S-MH-1494 A8 10.1 6.3 16.4 0.0 S-MH-1795 A9 7.6 15.8 19.3 0.0 S-MH-2333 B1 9.8 7.1 13.3 0.0 S-MH-750 B1 9.6 7.1 13.3 0.0 S-MH-800 (1) Residential flows shown are prior to peaking. All residential flow was peaked within the model.P. 1 M:\Marysville\11447\ Modeling\Flows\Node input 2011 for modela 2700 gpad.xls] Marysville Sewer Comprehensive Plan 2011 Model Input Sub-Basin Load 1: Residential Input1 (gpm) Load 2: Commercial Input (gpm) Load 3: I/I Input (gpm) Load 4: Fixed Flow (gpm) Input Node B2 0.0 0.0 0.0 0.0 S-MH-795 B3 7.1 12.3 12.2 0.0 S-MH-789 B4 2.4 0.0 1.7 0.0 S-MH-1648 B5 1.5 0.0 1.5 0.0 MH-216 CE1 5.6 0.0 7.7 0.0 S-MH-1522 CE2 10.4 0.4 11.0 0.0 S-MH-1751 CE3 11.8 0.0 16.8 0.0 S-MH-1745 CE4 7.8 0.0 11.9 0.0 S-MH-1743 CE5 8.3 0.0 0.0 0.0 S-MH-1753 CE5 3.7 0.0 29.2 0.0 S-MH-1688 CE5-1 10.6 0.0 12.5 0.0 S-MH-1679 CE5-1 2.9 0.0 12.8 0.0 S-MH-1671 CE5-2 10.8 186.3 81.6 0.0 S-MH-1657 CE5-3 29.0 0.0 39.9 0.0 S-MH-1964 CE5-4 4.8 5.9 10.6 0.0 S-MH-3757 CE5-5 5.7 0.0 7.6 0.0 S-MH-1973 CE5-6 9.8 0.0 11.9 0.0 S-MH-1943 CE5-7 65.3 26.5 79.6 0.0 S-MH-4642 CE6 19.0 0.0 24.6 0.0 S-MH-2074 CE7 32.3 0.0 33.9 0.0 S-MH-2117 CE8 15.5 0.0 15.3 0.0 S-MH-2062 CE9 14.4 0.0 15.8 0.0 S-MH-2281 CW1 25.7 90.0 27.4 0.0 S-MH-3577 CW1 25.4 0.0 54.7 0.0 S-MH-483 CW10 15.7 3.2 21.7 0.0 S-MH-1513 CW11 1.8 29.3 15.1 11.4 S-MH-1765 CW11-1 2.2 0.0 13.7 0.0 S-MH-1775 CW11-1 2.2 52.7 13.7 0.0 S-MH-4716 CW12 5.4 34.9 23.7 0.0 S-MH-1537 CW13 12.3 62.5 33.0 5.9 S-MH-1800 CW14 5.6 16.3 8.9 0.0 S-MH-1852 CW14 2.3 16.3 8.9 0.0 S-MH-1849 CW15 1.3 7.1 3.4 0.0 S-MH-1834 CW15 1.3 0.0 3.4 0.0 S-MH-4377 CW2 13.8 9.9 16.7 0.0 S-MH-481 CW2 6.8 9.9 8.3 0.0 S-MH-477 CW3 47.5 16.9 58.7 7.4 S-MH-308 CW4 15.0 56.4 30.2 0.0 S-MH-449 CW5 0.8 47.8 20.2 7.3 S-MH-4089 CW6 26.5 5.8 19.2 0.0 S-MH-1369 CW7 14.9 64.0 42.4 0.0 S-MH-246 CW8 14.2 0.0 16.9 0.0 S-MH-1564 CW8 14.1 45.7 16.9 0.0 S-MH-1567 CW9 0.1 28.9 23.9 0.0 S-MH-1568 D1 3.8 7.7 16.1 0.0 S-MH-533 D10 12.0 0.0 16.0 0.0 S-MH-2007 D10-1 0.0 0.0 0.0 0.0 S-MH-3916 D10-2 16.3 0.0 18.2 0.0 S-MH-4192 D10-3 0.0 0.0 0.0 0.0 S-MH-4546 D10-4 0.0 0.0 0.0 0.0 S-MH-4864 D10-5 0.0 0.0 0.0 0.0 S-MH-905 D10-6 20.9 0.0 20.3 0.0 S-MH-4545 D11 9.1 0.0 20.7 0.0 S-MH-1924 D12 28.3 0.0 46.2 0.0 S-MH-3732 D2 6.3 0.0 7.4 0.0 S-MH-624 D3 10.6 10.7 21.8 0.0 S-MH-641 D3-1 8.7 0.0 16.6 0.0 S-MH-1305 D3-1 8.7 0.0 16.6 0.0 S-MH-635 D3-10 16.0 0.0 18.5 0.0 S-MH-40 D3-10 16.0 0.0 18.5 0.0 S-MH-975 D3-11 51.8 0.0 54.3 0.0 S-MH-4872 D3-12 48.7 0.0 70.7 0.0 S-MH-110 D3-13 6.3 0.0 14.8 0.0 S-MH-1318 D3-2 16.6 0.0 15.0 0.0 S-MH-1209 D3-3 13.9 0.0 19.4 0.0 S-MH-1216 D3-4 14.7 0.0 13.1 0.0 S-MH-3697 D3-5 31.5 3.3 35.6 0.0 S-MH-3382 D3-5 21.0 1.6 23.7 0.0 S-MH-3357 D3-5 17.5 1.6 19.8 0.0 S-MH-3381 D3-6 5.2 0.0 13.5 0.0 S-MH-3309 D3-7 15.9 0.0 16.3 0.0 S-MH-3294 D3-8 28.8 0.0 23.0 0.0 MH-162 (1) Residential flows shown are prior to peaking. All residential flow was peaked within the model.P. 2 M:\Marysville\11447\ Modeling\Flows\Node input 2011 for modela 2700 gpad.xls] Marysville Sewer Comprehensive Plan 2011 Model Input Sub-Basin Load 1: Residential Input1 (gpm) Load 2: Commercial Input (gpm) Load 3: I/I Input (gpm) Load 4: Fixed Flow (gpm) Input Node D3-8 28.8 0.0 23.0 0.0 S-MH-3672 D3-9 15.8 0.0 20.8 0.0 S-MH-3677 D3-9 15.7 0.0 20.8 0.0 S-MH-3705 D4 17.6 0.0 20.6 0.0 S-MH-844 D5 22.9 6.2 30.1 0.0 S-MH-669 D5-1 4.3 11.4 13.0 6.5 S-MH-852 D5-2 19.8 11.5 21.7 0.0 S-MH-853 D5-2 19.7 0.0 21.7 0.0 S-MH-916 D6 26.4 0.0 38.8 0.0 S-MH-706 D6-1 11.0 0.0 14.9 0.0 S-MH-717 D6-2 94.0 6.0 118.9 0.0 S-MH-906 D6-3 12.3 0.0 21.5 0.0 S-MH-898 D6-4 19.6 0.0 22.8 0.0 S-MH-1006 D6-5 32.9 0.0 30.8 0.0 S-MH-1071 D7 6.1 0.0 12.5 0.0 S-MH-1609 D7-1 16.6 0.0 9.0 0.0 S-MH-1591 D7-2 18.3 0.0 15.4 0.0 S-MH-1593 D8 6.5 5.2 15.5 0.0 S-MH-2001 D9 18.1 0.0 32.8 0.0 S-MH-924 D9-1 15.3 0.0 17.2 0.0 S-MH-1169 F1 0.9 0.0 1.8 0.0 S-MH-2362 F10 0.0 19.0 24.8 0.0 S-MH-2705 F10 0.0 75.9 12.3 0.0 MH-102 F11 0.1 43.6 18.3 0.0 S-MH-2589 F12 0.3 47.6 19.2 0.0 S-MH-2719 F12 0.3 47.6 19.2 0.0 S-MH-2596 F13 0.1 67.3 31.5 0.0 S-MH-3462 F13-1 0.0 0.9 16.7 0.0 S-MH-4564 F13-1 0.0 0.9 16.7 0.0 S-MH-4568 F13-2 4.5 0.0 14.7 0.0 S-MH-4576 F14 0.6 32.9 10.8 54.2 S-MH-3847 F14 0.4 0.0 10.8 0.0 S-MH-3845 F14 0.4 32.9 10.8 0.0 S-MH-3467 F15 3.6 25.6 11.4 0.0 S-MH-3470 F15 3.5 25.6 11.5 0.0 S-MH-3044 F15 3.3 12.8 11.5 0.0 S-MH-3638 F16 0.3 8.6 9.4 0.0 S-MH-3527 F16 0.3 8.6 9.4 0.0 S-MH-3525 F17 0.3 19.6 8.2 0.0 S-MH-3531 F17 0.2 19.6 8.2 0.0 S-MH-3533 F18 0.0 24.6 20.7 0.0 S-MH-3538 F18 0.0 24.6 20.7 0.0 S-MH-3109 F19 0.0 36.4 18.6 0.0 S-MH-3536 F19 0.0 54.6 18.6 5.8 S-MH-3498 F2 1.6 0.0 2.3 0.0 S-MH-2363 F20 18.1 98.9 25.9 0.0 S-MH-3506 F20 5.4 0.0 31.1 0.0 S-MH-3510 F21 55.5 3.4 35.1 0.0 S-MH-3205 F22 3.2 0.0 12.0 0.0 S-MH-3155 F22 3.2 57.0 12.0 0.0 S-MH-3148 F22 3.2 0.0 11.9 0.0 S-MH-4910 F22-1 2.1 4.7 66.6 0.0 S-MH-3239 F3 10.1 0.0 24.7 0.0 S-MH-2364 F4 30.0 0.0 38.8 0.0 S-MH-2708 F5 8.5 34.8 23.7 0.0 S-MH-2357 F5 2.1 34.8 5.9 0.0 S-MH-2356 F6 5.6 0.0 7.0 0.0 S-MH-3860 F7 2.6 28.3 17.1 0.0 MH-166 F8 1.1 17.8 11.1 0.0 S-MH-2760 F9 0.0 35.6 14.8 5.3 S-MH-2684 G1 19.4 59.0 49.5 0.0 S-MH-428 G2 11.9 12.0 16.1 0.0 S-MH-420 G2 11.9 0.0 16.1 0.0 S-MH-464 G3 0.1 144.2 36.9 0.0 S-MH-2476 G4 0.0 42.2 17.1 0.0 S-MH-2540 G5 18.0 0.0 22.2 0.0 S-MH-2482 G6 16.3 0.0 19.0 0.0 S-MH-2509 G7 8.2 0.0 5.3 0.0 S-MH-2548 G8 0.0 19.7 8.0 0.0 S-MH-2550 Total (gpm):2,324 2,414 3,818 128 (1) Residential flows shown are prior to peaking. All residential flow was peaked within the model.P. 3 M:\Marysville\11447\ Modeling\Flows\Node input 2011 for modela 2700 gpad.xls] Marysville Sewer Comprehensive Plan 2017 Model Input Sub-Basin Load 1: Residential Input1 (gpm) Load 2: Commercial Input (gpm) Load 3: I/I Input (gpm) Load 4: Fixed Flow (gpm) Input Node A1 0.1 20.9 7.2 0.0 S-MH-3559 A10 13.5 0.0 0.0 0.0 S-MH-2323 A10 11.7 0.0 14.9 0.0 S-MH-2141 A10 11.7 0.0 14.9 0.0 S-MH-2332 A11 17.5 5.7 10.8 0.0 S-MH-2189 A12 14.4 0.0 10.6 0.0 S-MH-2290 A12 14.4 0.0 10.6 0.0 S-MH-2198 A12-1 15.4 0.0 12.9 0.0 S-MH-2300 A12-2 39.6 0.0 20.5 0.0 S-MH-2225 A12-3 6.1 0.0 6.7 0.0 S-MH-3632 A12-3 6.2 0.0 6.7 0.0 S-MH-2259 A12-3 16.4 0.0 0.0 0.0 S-MH-2235 A12-4 14.6 0.0 7.3 0.0 MH-231 A13 10.6 2.2 10.1 0.0 S-MH-2315 A13 25.4 2.2 20.3 0.0 S-MH-3791 A14 9.2 0.0 12.9 0.0 S-MH-2386 A15 9.4 0.0 30.0 0.0 S-MH-2396 A15 9.4 0.0 30.0 0.0 S-MH-2419 A16 9.6 0.0 9.3 0.0 S-MH-2402 A16 9.6 15.8 9.3 0.0 S-MH-2401 A16-1 30.3 0.0 12.2 0.0 S-MH-4810 A16-1 30.3 0.0 12.2 0.0 S-MH-4742 A17 15.9 1.1 21.0 0.0 S-MH-2739 A18 8.8 0.0 8.4 0.0 S-MH-2743 A18 11.0 0.0 11.5 0.0 S-MH-2742 A18 8.8 0.0 8.4 0.0 S-MH-2856 A18-1 6.8 0.0 1.5 0.0 S-MH-2915 A18-2 12.6 0.0 11.9 0.0 S-MH-2865 A18-3 8.3 0.0 5.2 0.0 S-MH-2840 A19 42.7 0.0 41.0 0.0 S-MH-2733 A2 23.7 1.9 20.5 0.0 S-MH-336 A20 13.4 0.0 12.4 0.0 S-MH-2887 A20 13.4 0.0 12.4 0.0 MH-4 A20 13.4 0.0 12.4 0.0 S-MH-2727 A21 2.6 0.0 18.4 0.0 S-MH-2597 A21 5.9 85.8 23.6 0.0 S-MH-2980 A21 2.8 85.8 11.8 0.0 S-MH-2772 A22 12.4 0.0 7.4 0.0 S-MH-2795 A22 12.4 1.6 7.4 0.0 S-MH-2781 A22 5.1 1.6 7.4 0.0 S-MH-3595 A23 13.8 24.8 11.3 0.0 S-MH-2919 A23 13.8 6.2 11.3 0.0 S-MH-2969 A24 39.2 0.0 3.4 0.0 S-MH-3016 A24-1 0.1 64.7 2.2 0.0 S-MH-2815 A24-1 0.1 64.7 2.2 0.0 S-MH-3022 A24-2 0.0 0.0 0.0 0.0 S-MH-3614 A24-2 0.0 150.0 0.0 0.0 S-MH-3619 A24-3 0.0 135.0 0.0 0.0 S-MH-3622 A24-3 0.0 0.0 0.0 0.0 S-MH-3617 A24-4 7.6 0.0 3.2 0.0 S-MH-3080 A24-4 7.6 80.6 3.2 0.0 S-MH-3099 A24-4 7.7 0.0 3.2 0.0 S-MH-3077 A24-5 0.4 187.5 1.5 0.0 S-MH-2814 A25 0.3 168.8 4.3 0.0 S-MH-3837 A25-1 0.3 365.6 13.2 0.0 S-MH-3143 A26 0.7 36.8 3.2 0.0 S-MH-3422 A26 0.9 73.6 3.2 28.3 S-MH-3838 A26 0.7 36.8 3.2 0.0 S-MH-3139 A27 0.6 116.5 22.2 0.0 S-MH-3415 A27 0.1 0.0 5.6 0.0 S-MH-3403 A28 7.7 0.0 6.8 0.0 S-MH-3430 A28 15.3 0.0 13.7 0.0 S-MH-3443 A4 17.3 1.4 10.2 0.0 S-MH-357 A5 23.9 0.9 13.0 0.0 S-MH-277 A6 23.2 3.0 13.8 0.0 MH-22 A6 24.3 3.0 13.8 0.0 S-MH-3768 A6 23.2 0.0 13.8 0.0 S-MH-1548 A7 13.6 0.0 19.5 0.0 S-MH-1455 A7 9.7 0.4 0.0 0.0 S-MH-1494 A8 14.4 6.3 13.9 0.0 S-MH-1795 A9 10.0 15.8 16.4 0.0 S-MH-2333 B1 16.1 9.3 11.3 0.0 S-MH-750 B1 15.7 9.3 11.3 0.0 S-MH-800 (1) Residential flows shown are prior to peaking. All residential flow was peaked within the model.P. 1 M:\Marysville\11447\ Modeling\Flows\Node input 2017 for modela 2700 gpad.xls Marysville Sewer Comprehensive Plan 2017 Model Input Sub-Basin Load 1: Residential Input1 (gpm) Load 2: Commercial Input (gpm) Load 3: I/I Input (gpm) Load 4: Fixed Flow (gpm) Input Node B2 6.9 0.0 0.0 0.0 S-MH-795 B3 11.5 12.3 10.3 0.0 S-MH-789 B4 6.2 0.0 1.4 0.0 S-MH-1648 B5 5.4 0.0 1.3 0.0 MH-216 CE1 7.6 0.0 6.6 0.0 S-MH-1522 CE2 15.4 0.4 9.3 0.0 S-MH-1751 CE3 14.1 0.0 14.3 0.0 S-MH-1745 CE4 9.1 0.0 10.0 0.0 S-MH-1743 CE5 11.1 0.0 0.0 0.0 S-MH-1753 CE5 4.9 0.0 24.7 0.0 S-MH-1688 CE5-1 12.4 0.0 10.6 0.0 S-MH-1679 CE5-1 3.4 0.0 10.8 0.0 S-MH-1671 CE5-2 10.8 186.3 62.2 0.0 S-MH-1657 CE5-3 30.2 0.0 33.8 0.0 S-MH-1964 CE5-4 4.8 13.2 9.0 0.0 S-MH-3757 CE5-5 6.7 0.0 6.5 0.0 S-MH-1973 CE5-6 9.9 0.0 10.1 0.0 S-MH-1943 CE5-7 79.1 101.5 67.4 0.0 S-MH-4642 CE6 22.5 0.0 20.8 0.0 S-MH-2074 CE7 32.9 0.0 28.7 0.0 S-MH-2117 CE8 15.5 0.0 12.9 0.0 S-MH-2062 CE9 14.5 1.9 13.3 0.0 S-MH-2281 CW1 31.1 90.0 46.3 0.0 S-MH-3577 CW1 31.4 0.0 23.2 0.0 S-MH-483 CW10 21.6 9.5 18.4 0.0 S-MH-1513 CW11 7.8 29.3 12.7 13.2 S-MH-1765 CW11-1 12.6 0.0 11.6 0.0 S-MH-1775 CW11-1 12.6 52.7 11.6 0.0 S-MH-4716 CW12 6.9 44.8 20.1 0.0 S-MH-1537 CW13 13.1 62.5 27.9 6.9 S-MH-1800 CW14 8.9 16.3 7.6 0.0 S-MH-1852 CW14 3.7 16.3 7.6 0.0 S-MH-1849 CW15 17.3 18.0 2.9 0.0 S-MH-1834 CW15 17.3 0.0 2.9 0.0 S-MH-4377 CW2 6.8 11.1 7.0 0.0 S-MH-481 CW2 13.8 11.1 14.1 0.0 S-MH-477 CW3 55.4 16.9 49.7 8.6 S-MH-308 CW4 18.3 64.3 25.6 0.0 S-MH-449 CW5 0.8 48.4 17.1 8.5 S-MH-4089 CW6 32.1 6.9 16.3 0.0 S-MH-1369 CW7 15.3 87.5 35.9 0.0 S-MH-246 CW8 15.4 0.0 14.3 0.0 S-MH-1564 CW8 15.3 47.7 14.3 0.0 S-MH-1567 CW9 0.1 46.0 20.0 0.0 S-MH-1568 D1 4.5 7.7 13.6 0.0 S-MH-533 D10 12.0 0.0 13.5 0.0 S-MH-2007 D10-1 3.0 43.1 0.0 0.0 S-MH-3916 D10-2 20.7 123.8 15.4 0.0 S-MH-4192 D10-3 5.1 0.0 0.0 0.0 S-MH-4865 D10-4 4.9 0.0 0.0 0.0 S-MH-4864 D10-5 4.2 20.6 0.0 0.0 S-MH-1088 D10-6 35.6 0.0 17.2 0.0 S-MH-4545 D11 9.1 0.0 17.5 0.0 S-MH-1924 D12 30.4 0.0 39.1 0.0 S-MH-3732 D2 6.9 0.0 6.2 0.0 S-MH-624 D3 12.6 10.7 18.4 0.0 S-MH-641 D3-1 10.3 0.0 14.0 0.0 S-MH-1305 D3-1 10.3 0.0 14.0 0.0 S-MH-635 D3-10 18.8 0.0 15.7 0.0 S-MH-40 D3-10 18.8 0.0 15.7 0.0 S-MH-975 D3-11 57.4 0.0 45.9 0.0 S-MH-4872 D3-12 60.8 0.0 59.8 0.0 S-MH-110 D3-13 9.7 0.0 12.5 0.0 S-MH-1318 D3-2 17.0 0.0 12.7 0.0 S-MH-1209 D3-3 16.6 0.0 16.4 0.0 S-MH-1216 D3-4 18.0 0.0 11.1 0.0 S-MH-3697 D3-5 25.5 3.3 20.1 0.0 S-MH-3382 D3-5 38.2 1.6 30.1 0.0 S-MH-3357 D3-5 21.2 1.6 16.7 0.0 S-MH-3381 D3-6 7.1 2.8 11.4 0.0 S-MH-3309 D3-7 19.3 0.0 13.8 0.0 S-MH-3294 D3-8 28.8 0.0 19.4 0.0 MH-162 (1) Residential flows shown are prior to peaking. All residential flow was peaked within the model.P. 2 M:\Marysville\11447\ Modeling\Flows\Node input 2017 for modela 2700 gpad.xls Marysville Sewer Comprehensive Plan 2017 Model Input Sub-Basin Load 1: Residential Input1 (gpm) Load 2: Commercial Input (gpm) Load 3: I/I Input (gpm) Load 4: Fixed Flow (gpm) Input Node D3-8 28.8 0.0 19.4 0.0 S-MH-3672 D3-9 18.3 0.0 17.6 0.0 S-MH-3677 D3-9 18.3 0.0 17.6 0.0 S-MH-3705 D4 17.6 0.0 17.5 0.0 S-MH-844 D5 23.5 6.2 25.5 0.0 S-MH-669 D5-1 5.0 11.4 11.0 7.5 S-MH-852 D5-2 20.0 11.5 18.4 0.0 S-MH-853 D5-2 20.0 0.0 18.4 0.0 S-MH-916 D6 28.1 0.0 32.8 0.0 S-MH-706 D6-1 11.3 0.0 12.6 0.0 S-MH-717 D6-2 104.6 6.0 100.6 0.0 S-MH-906 D6-3 12.6 0.0 18.2 0.0 S-MH-898 D6-4 19.7 0.0 19.3 0.0 S-MH-1006 D6-5 38.7 37.5 26.0 0.0 S-MH-1071 D7 6.3 0.0 10.5 0.0 S-MH-1609 D7-1 16.6 0.0 7.6 0.0 S-MH-1591 D7-2 18.3 0.0 13.0 0.0 S-MH-1593 D8 6.7 5.2 13.1 0.0 S-MH-2001 D9 19.9 0.0 27.7 0.0 S-MH-924 D9-1 17.9 0.0 14.6 0.0 S-MH-1169 F1 2.1 0.0 1.5 0.0 S-MH-2362 F10 0.0 29.3 21.0 0.0 S-MH-2705 F10 0.0 117.2 10.4 0.0 MH-102 F11 0.1 54.9 15.5 0.0 S-MH-2589 F12 0.3 99.8 16.2 0.0 S-MH-2719 F12 0.3 99.8 16.2 0.0 S-MH-2596 F13 0.1 132.9 26.7 0.0 S-MH-3462 F13-1 0.1 113.4 14.1 0.0 S-MH-4564 F13-1 0.1 113.4 14.1 0.0 S-MH-4568 F13-2 5.4 123.8 12.5 0.0 S-MH-4576 F14 0.8 79.8 9.1 63.1 S-MH-3847 F14 0.6 0.0 9.2 0.0 S-MH-3845 F14 0.6 79.8 9.2 0.0 S-MH-3467 F15 3.4 48.1 9.7 0.0 S-MH-3470 F15 3.5 48.1 9.7 0.0 S-MH-3044 F15 3.6 24.1 9.6 0.0 S-MH-3638 F16 0.3 47.8 7.9 0.0 S-MH-3527 F16 0.3 47.8 7.9 0.0 S-MH-3525 F17 0.4 38.3 7.0 0.0 S-MH-3531 F17 0.4 38.3 7.0 0.0 S-MH-3533 F18 0.0 35.9 11.0 0.0 S-MH-3538 F18 0.0 35.9 11.0 0.0 S-MH-3109 F19 0.0 36.4 14.6 0.0 S-MH-3536 F19 0.0 54.6 14.6 6.8 S-MH-3498 F2 5.8 0.0 1.9 0.0 S-MH-2363 F20 6.3 140.1 26.3 0.0 S-MH-3506 F20 21.1 0.0 21.9 0.0 S-MH-3510 F21 65.1 37.1 29.7 0.0 S-MH-3205 F22 6.5 0.0 10.1 0.0 S-MH-3155 F22 6.5 57.0 10.2 0.0 S-MH-3148 F22 6.5 0.0 10.2 0.0 S-MH-4910 F22-1 5.0 197.4 56.4 0.0 S-MH-3239 F3 10.1 0.0 20.9 0.0 S-MH-2364 F4 32.7 0.0 32.8 0.0 S-MH-2708 F5 11.2 44.2 20.0 0.0 S-MH-2357 F5 2.8 44.2 5.0 0.0 S-MH-2356 F6 5.6 0.0 5.9 0.0 S-MH-3860 F7 3.7 54.5 14.5 0.0 MH-166 F8 1.6 34.7 9.4 0.0 S-MH-2760 F9 0.0 58.1 12.5 6.2 S-MH-2684 G1 22.9 69.4 41.9 0.0 S-MH-428 G2 15.3 21.4 13.7 0.0 S-MH-420 G2 15.3 0.0 13.7 0.0 S-MH-464 G3 0.1 144.2 31.3 0.0 S-MH-2476 G4 0.4 51.5 14.5 0.0 S-MH-2540 G5 18.0 0.0 18.8 0.0 S-MH-2482 G6 16.3 0.0 16.1 0.0 S-MH-2509 G7 13.2 54.0 4.5 0.0 S-MH-2548 G8 0.6 19.7 6.8 0.0 S-MH-2550 Total (gpm):2,840.5 5,600.3 3,183.2 149.2 (1) Residential flows shown are prior to peaking. All residential flow was peaked within the model.P. 3 M:\Marysville\11447\ Modeling\Flows\Node input 2017 for modela 2700 gpad.xls Marysville Sewer Comprehensive Plan 2031 Model Input Sub-Basin Load 1: Residential Input1 (gpm) Load 2: Commercial Input (gpm) Load 3: I/I Input (gpm) Load 4: Fixed Flow (gpm) Input Node A1 1.0 20.9 9.5 0.0 S-MH-3559 A10 16.2 0.0 0.0 0.0 S-MH-2323 A10 14.0 0.0 19.8 0.0 S-MH-2141 A10 14.0 0.0 19.8 0.0 S-MH-2332 A11 18.9 5.7 14.3 0.0 S-MH-2189 A12 16.9 0.0 14.0 0.0 S-MH-2290 A12 16.9 0.0 14.0 0.0 S-MH-2198 A12-1 15.0 0.0 17.1 0.0 S-MH-2300 A12-2 39.4 0.0 27.3 0.0 S-MH-2225 A12-3 6.6 0.0 8.9 0.0 S-MH-3632 A12-3 6.8 0.0 8.9 0.0 S-MH-2259 A12-3 17.8 0.0 0.0 0.0 S-MH-2235 A12-4 17.6 0.0 9.7 0.0 MH-231 A13 10.5 2.2 13.5 0.0 S-MH-2315 A13 25.2 2.2 27.0 0.0 S-MH-3791 A14 10.8 0.0 17.1 0.0 S-MH-2386 A15 12.0 0.0 30.0 0.0 S-MH-2396 A15 12.0 0.0 30.0 0.0 S-MH-2419 A16 14.2 0.0 12.4 0.0 S-MH-2402 A16 14.2 15.8 12.4 0.0 S-MH-2401 A16-1 42.6 0.0 16.2 0.0 S-MH-4810 A16-1 42.6 0.0 16.2 0.0 S-MH-4742 A17 21.8 1.1 28.0 0.0 S-MH-2739 A18 8.6 0.0 11.2 0.0 S-MH-2743 A18 10.7 0.0 15.3 0.0 S-MH-2742 A18 8.6 0.0 11.2 0.0 S-MH-2856 A18-1 17.3 0.0 2.0 0.0 S-MH-2915 A18-2 12.0 0.0 14.0 0.0 S-MH-2865 A18-3 14.3 0.0 6.9 0.0 S-MH-2840 A19 58.4 0.0 54.5 0.0 S-MH-2733 A2 25.5 1.9 20.5 0.0 S-MH-336 A20 14.8 0.0 16.4 0.0 S-MH-2887 A20 14.8 0.0 16.4 0.0 MH-4 A20 14.8 0.0 16.4 0.0 S-MH-2727 A21 2.6 0.0 24.4 0.0 S-MH-2597 A21 5.9 85.8 31.4 0.0 S-MH-2980 A21 2.8 85.8 15.7 0.0 S-MH-2772 A22 15.2 0.0 9.9 0.0 S-MH-2795 A22 15.2 1.6 9.9 0.0 S-MH-2781 A22 6.2 1.6 9.9 0.0 S-MH-3595 A23 20.8 24.8 15.0 0.0 S-MH-2919 A23 20.9 6.2 15.0 0.0 S-MH-2969 A24 37.2 0.0 4.5 0.0 S-MH-3016 A24-1 0.2 64.7 2.9 0.0 S-MH-2815 A24-1 0.2 64.7 2.9 0.0 S-MH-3022 A24-2 0.0 0.0 0.0 0.0 S-MH-3614 A24-2 0.0 150.0 0.0 0.0 S-MH-3619 A24-3 0.0 135.0 0.0 0.0 S-MH-3622 A24-3 0.0 0.0 0.0 0.0 S-MH-3617 A24-4 7.3 0.0 4.2 0.0 S-MH-3080 A24-4 7.3 80.6 4.2 0.0 S-MH-3099 A24-4 7.3 0.0 4.2 0.0 S-MH-3077 A24-5 0.7 187.5 2.0 0.0 S-MH-2814 A25 0.5 168.8 5.7 0.0 S-MH-3837 A25-1 0.4 365.6 17.5 0.0 S-MH-3143 A26 0.7 36.8 4.2 0.0 S-MH-3422 A26 1.0 73.6 4.2 37.5 S-MH-3838 A26 0.7 36.8 4.2 0.0 S-MH-3139 A27 0.8 116.5 29.5 0.0 S-MH-3415 A27 0.2 0.0 7.4 0.0 S-MH-3403 A28 10.1 0.0 9.1 0.0 S-MH-3430 A28 20.2 0.0 18.2 0.0 S-MH-3443 A4 19.3 1.4 13.5 0.0 S-MH-357 A5 27.1 0.9 17.3 0.0 S-MH-277 A6 27.3 3.0 18.3 0.0 MH-22 A6 28.6 3.0 18.3 0.0 S-MH-3768 A6 27.3 0.0 18.3 0.0 S-MH-1548 A7 19.8 0.0 25.9 0.0 S-MH-1455 A7 14.2 0.4 0.0 0.0 S-MH-1494 A8 18.6 6.3 18.5 0.0 S-MH-1795 A9 11.9 15.8 19.9 0.0 S-MH-2333 B1 22.8 9.3 15.0 0.0 S-MH-750 B1 22.3 9.3 15.0 0.0 S-MH-800 (1) Residential flows shown are prior to peaking. All residential flow was peaked within the model.P.1 M:\Marysville\11447\ Modeling\Flows\Node input 2031 for modela 2700 gpad Aug.xls Marysville Sewer Comprehensive Plan 2031 Model Input Sub-Basin Load 1: Residential Input1 (gpm) Load 2: Commercial Input (gpm) Load 3: I/I Input (gpm) Load 4: Fixed Flow (gpm) Input Node B2 17.9 0.0 0.0 0.0 S-MH-795 B3 19.5 12.3 13.7 0.0 S-MH-789 B4 11.5 0.0 1.9 0.0 S-MH-1648 B5 15.1 0.0 1.7 0.0 MH-216 CE1 9.6 0.0 8.7 0.0 S-MH-1522 CE2 22.4 0.4 12.4 0.0 S-MH-1751 CE3 15.9 0.0 18.9 0.0 S-MH-1745 CE4 9.7 0.0 13.3 0.0 S-MH-1743 CE5 16.3 0.0 0.0 0.0 S-MH-1753 CE5 7.2 0.0 32.9 0.0 S-MH-1688 CE5-1 14.1 0.0 14.1 0.0 S-MH-1679 CE5-1 3.9 0.0 14.4 0.0 S-MH-1671 CE5-2 10.3 186.3 62.2 0.0 S-MH-1657 CE5-3 29.2 0.0 44.9 0.0 S-MH-1964 CE5-4 4.5 13.2 11.9 0.0 S-MH-3757 CE5-5 6.7 0.0 8.6 0.0 S-MH-1973 CE5-6 9.4 0.0 13.4 0.0 S-MH-1943 CE5-7 140.2 101.5 89.5 0.0 S-MH-4642 CE6 25.8 0.0 27.7 0.0 S-MH-2074 CE7 31.7 0.0 38.1 0.0 S-MH-2117 CE8 14.7 0.0 15.2 0.0 S-MH-2062 CE9 14.0 1.9 17.7 0.0 S-MH-2281 CW1 32.7 90.0 61.5 0.0 S-MH-3577 CW1 33.0 0.0 30.8 0.0 S-MH-483 CW10 26.5 9.5 24.4 0.0 S-MH-1513 CW11 20.9 29.3 16.9 17.6 S-MH-1765 CW11-1 43.7 0.0 15.4 0.0 S-MH-1775 CW11-1 43.7 52.7 15.4 0.0 S-MH-4716 CW12 9.4 44.8 26.7 0.0 S-MH-1537 CW13 14.3 62.5 29.1 9.1 S-MH-1800 CW14 21.2 16.3 10.0 0.0 S-MH-1852 CW14 8.8 16.3 10.0 0.0 S-MH-1849 CW15 62.2 18.0 3.8 0.0 S-MH-1834 CW15 62.2 0.0 3.8 0.0 S-MH-4377 CW2 6.5 11.1 9.3 0.0 S-MH-481 CW2 13.1 11.1 18.8 0.0 S-MH-477 CW3 58.2 16.9 56.5 11.5 S-MH-308 CW4 19.8 64.3 34.0 0.0 S-MH-449 CW5 0.8 48.4 18.7 11.3 S-MH-4089 CW6 34.7 6.9 21.6 0.0 S-MH-1369 CW7 15.6 87.5 42.4 0.0 S-MH-246 CW8 15.3 0.0 19.0 0.0 S-MH-1564 CW8 15.3 47.7 19.0 0.0 S-MH-1567 CW9 0.1 46.0 20.0 0.0 S-MH-1568 D1 5.4 7.7 18.1 0.0 S-MH-533 D10 11.4 0.0 18.0 0.0 S-MH-2007 D10-1 33.0 43.1 0.0 0.0 S-MH-3916 D10-2 66.3 123.8 20.4 0.0 S-MH-4192 D10-3 36.2 0.0 0.0 0.0 S-MH-4546 D10-4 29.7 0.0 0.0 0.0 S-MH-4864 D10-5 12.3 20.6 0.0 0.0 S-MH-905 D10-6 62.0 0.0 22.8 0.0 S-MH-4545 D11 8.7 0.0 18.9 0.0 S-MH-1924 D12 28.9 0.0 49.3 0.0 S-MH-3732 D2 6.7 0.0 8.3 0.0 S-MH-624 D3 13.2 10.7 24.5 0.0 S-MH-641 D3-1 11.5 0.0 18.6 0.0 S-MH-1305 D3-1 11.5 0.0 18.6 0.0 S-MH-635 D3-10 18.4 0.0 20.8 0.0 S-MH-40 D3-10 18.4 0.0 20.8 0.0 S-MH-975 D3-11 55.9 0.0 61.0 0.0 S-MH-4872 D3-12 95.6 0.0 79.5 0.0 S-MH-110 D3-13 22.1 0.0 16.6 0.0 S-MH-1318 D3-2 16.3 0.0 16.9 0.0 S-MH-1209 D3-3 17.9 0.0 21.8 0.0 S-MH-1216 D3-4 27.9 0.0 14.7 0.0 S-MH-3697 D3-5 33.4 3.3 26.7 0.0 S-MH-3382 D3-5 50.1 1.6 40.0 0.0 S-MH-3357 D3-5 27.8 1.6 22.2 0.0 S-MH-3381 D3-6 15.3 2.8 15.1 0.0 S-MH-3309 D3-7 21.3 0.0 18.4 0.0 S-MH-3294 D3-8 27.4 0.0 25.8 0.0 MH-162 (1) Residential flows shown are prior to peaking. All residential flow was peaked within the model.P.2 M:\Marysville\11447\ Modeling\Flows\Node input 2031 for modela 2700 gpad Aug.xls Marysville Sewer Comprehensive Plan 2031 Model Input Sub-Basin Load 1: Residential Input1 (gpm) Load 2: Commercial Input (gpm) Load 3: I/I Input (gpm) Load 4: Fixed Flow (gpm) Input Node D3-8 27.4 0.0 25.8 0.0 S-MH-3672 D3-9 17.5 0.0 22.2 0.0 S-MH-3677 D3-9 17.5 0.0 22.2 0.0 S-MH-3705 D4 16.9 0.0 21.6 0.0 S-MH-844 D5 23.3 6.2 32.9 0.0 S-MH-669 D5-1 6.6 11.4 14.6 10.0 S-MH-852 D5-2 19.1 11.5 21.8 0.0 S-MH-853 D5-2 19.2 0.0 21.8 0.0 S-MH-916 D6 27.0 0.0 42.4 0.0 S-MH-706 D6-1 10.8 0.0 14.9 0.0 S-MH-717 D6-2 100.9 6.0 133.7 0.0 S-MH-906 D6-3 12.0 0.0 21.1 0.0 S-MH-898 D6-4 18.8 0.0 25.7 0.0 S-MH-1006 D6-5 57.9 37.5 34.6 0.0 S-MH-1071 D7 6.3 0.0 13.1 0.0 S-MH-1609 D7-1 15.8 0.0 10.2 0.0 S-MH-1591 D7-2 17.3 0.0 17.3 0.0 S-MH-1593 D8 6.5 5.2 15.8 0.0 S-MH-2001 D9 19.1 0.0 36.8 0.0 S-MH-924 D9-1 17.6 0.0 19.4 0.0 S-MH-1169 F1 5.4 0.0 2.0 0.0 S-MH-2362 F10 0.1 29.3 27.9 0.0 S-MH-2705 F10 0.0 117.2 13.8 0.0 MH-102 F11 0.1 54.9 20.6 0.0 S-MH-2589 F12 0.4 99.8 21.5 0.0 S-MH-2719 F12 0.4 99.8 21.5 0.0 S-MH-2596 F13 0.1 132.9 35.4 0.0 S-MH-3462 F13-1 8.6 113.4 18.7 0.0 S-MH-4564 F13-1 8.6 113.4 18.7 0.0 S-MH-4568 F13-2 6.4 123.8 16.5 0.0 S-MH-4576 F14 1.4 79.8 12.1 83.9 S-MH-3847 F14 1.0 0.0 12.2 0.0 S-MH-3845 F14 1.0 79.8 12.2 0.0 S-MH-3467 F15 3.3 48.1 12.9 0.0 S-MH-3470 F15 3.4 48.1 12.9 0.0 S-MH-3044 F15 3.6 24.1 12.8 0.0 S-MH-3638 F16 0.3 47.8 10.5 0.0 S-MH-3527 F16 0.3 47.8 10.5 0.0 S-MH-3525 F17 0.8 38.3 9.3 0.0 S-MH-3531 F17 0.7 38.3 9.3 0.0 S-MH-3533 F18 0.0 35.9 11.0 0.0 S-MH-3538 F18 0.0 35.9 11.0 0.0 S-MH-3109 F19 0.0 36.4 14.6 0.0 S-MH-3536 F19 0.0 54.6 14.6 9.0 S-MH-3498 F2 14.6 0.0 2.6 0.0 S-MH-2363 F20 10.5 140.1 35.0 0.0 S-MH-3506 F20 34.9 0.0 29.1 0.0 S-MH-3510 F21 72.7 37.1 39.5 0.0 S-MH-3205 F22 11.9 0.0 13.4 0.0 S-MH-3155 F22 11.9 57.0 13.5 0.0 S-MH-3148 F22 11.9 0.0 13.5 0.0 S-MH-4910 F22-1 51.0 197.4 74.9 0.0 S-MH-3239 F3 9.6 0.0 21.8 0.0 S-MH-2364 F4 37.2 0.0 43.6 0.0 S-MH-2708 F5 22.5 44.2 26.6 0.0 S-MH-2357 F5 5.6 44.2 6.7 0.0 S-MH-2356 F6 5.3 0.0 7.3 0.0 S-MH-3860 F7 8.9 54.5 19.3 0.0 MH-166 F8 5.6 34.7 12.5 0.0 S-MH-2760 F9 0.0 58.1 16.6 8.2 S-MH-2684 G1 29.6 69.4 55.7 0.0 S-MH-428 G2 29.3 21.4 18.1 0.0 S-MH-420 G2 29.3 0.0 18.1 0.0 S-MH-464 G3 0.1 144.2 41.5 0.0 S-MH-2476 G4 1.2 51.5 19.2 0.0 S-MH-2540 G5 17.1 0.0 24.9 0.0 S-MH-2482 G6 15.4 0.0 21.3 0.0 S-MH-2509 G7 26.1 54.0 6.0 0.0 S-MH-2548 G8 2.8 19.7 9.0 0.0 S-MH-2550 Total (gpm):3,790 5,600 4,094 198 (1) Residential flows shown are prior to peaking. All residential flow was peaked within the model.P.3 M:\Marysville\11447\ Modeling\Flows\Node input 2031 for modela 2700 gpad Aug.xls Marysville Sewer Comprehensive Plan Buildout Model Input Sub-Basin Load 1: Residential Input1 (gpm) Load 2: Commercial Input (gpm) Load 3: I/I Input (gpm) Load 4: Fixed Flow (gpm) Input Node A1 1.0 20.9 9.5 0.0 S-MH-3559 A10 16.2 0.0 0.0 0.0 S-MH-2323 A10 14.0 0.0 19.8 0.0 S-MH-2141 A10 14.0 0.0 19.8 0.0 S-MH-2332 A11 18.9 5.7 14.3 0.0 S-MH-2189 A12 16.9 0.0 14.0 0.0 S-MH-2290 A12 16.9 0.0 14.0 0.0 S-MH-2198 A12-1 15.0 0.0 17.1 0.0 S-MH-2300 A12-2 39.4 0.0 27.3 0.0 S-MH-2225 A12-3 6.6 0.0 8.9 0.0 S-MH-3632 A12-3 6.8 0.0 8.9 0.0 S-MH-2259 A12-3 17.8 0.0 0.0 0.0 S-MH-2235 A12-4 17.6 0.0 9.7 0.0 MH-231 A13 10.5 2.2 13.5 0.0 S-MH-2315 A13 25.2 2.2 27.0 0.0 S-MH-3791 A14 10.8 0.0 17.1 0.0 S-MH-2386 A15 12.0 0.0 30.0 0.0 S-MH-2396 A15 12.0 0.0 30.0 0.0 S-MH-2419 A16 14.2 0.0 12.4 0.0 S-MH-2402 A16 14.2 15.8 12.4 0.0 S-MH-2401 A16(Future)97.3 0.0 440.0 0.0 S-MH-4739 A16(Future)47.9 0.0 216.7 0.0 S-MH-3789 A16-1 42.6 0.0 16.2 0.0 S-MH-4810 A16-1 42.6 0.0 16.2 0.0 S-MH-4742 A17 21.8 1.1 28.0 0.0 S-MH-2739 A18 8.6 0.0 11.2 0.0 S-MH-2743 A18 10.7 0.0 15.3 0.0 S-MH-2742 A18 8.6 0.0 11.2 0.0 S-MH-2856 A18(Future)22.1 0.0 100.0 0.0 S-MH-2882 A18-1 17.3 0.0 2.0 0.0 S-MH-2915 A18-2 12.0 0.0 14.0 0.0 S-MH-2865 A18-3 14.3 0.0 6.9 0.0 S-MH-2840 A18-3(Future)19.7 0.0 88.9 0.0 S-MH-2843 A19 58.4 0.0 54.5 0.0 S-MH-2733 A2 25.5 1.9 20.5 0.0 S-MH-336 A20 14.8 0.0 16.4 0.0 S-MH-2887 A20 14.8 0.0 16.4 0.0 MH-4 A20 14.8 0.0 16.4 0.0 S-MH-2727 A21 2.6 0.0 24.4 0.0 S-MH-2597 A21 5.9 85.8 31.4 0.0 S-MH-2980 A21 2.8 85.8 15.7 0.0 S-MH-2772 A22 15.2 0.0 9.9 0.0 S-MH-2795 A22 15.2 1.6 9.9 0.0 S-MH-2781 A22 6.2 1.6 9.9 0.0 S-MH-3595 A23 20.8 24.8 15.0 0.0 S-MH-2919 A23 20.9 6.2 15.0 0.0 S-MH-2969 A24 37.2 0.0 4.5 0.0 S-MH-3016 A24(Future)249.7 0.0 1,130.0 0.0 S-MH-2816 A24-1 0.2 64.7 2.9 0.0 S-MH-2815 A24-1 0.2 64.7 2.9 0.0 S-MH-3022 A24-2 0.0 0.0 0.0 0.0 S-MH-3614 A24-2 0.0 150.0 0.0 0.0 S-MH-3619 A24-3 0.0 135.0 0.0 0.0 S-MH-3622 A24-3 0.0 0.0 0.0 0.0 S-MH-3617 A24-4 7.3 0.0 4.2 0.0 S-MH-3080 A24-4 7.3 80.6 4.2 0.0 S-MH-3099 A24-4 7.3 0.0 4.2 0.0 S-MH-3077 A24-5 0.7 187.5 2.0 0.0 S-MH-2814 A25 0.5 168.8 5.7 0.0 S-MH-3837 A25-1 0.4 365.6 17.5 0.0 S-MH-3143 A26 0.7 36.8 4.2 0.0 S-MH-3422 A26 1.0 73.6 4.2 37.5 S-MH-3838 A26 0.7 36.8 4.2 0.0 S-MH-3139 A27 0.8 116.5 29.5 0.0 S-MH-3415 A27 0.2 0.0 7.4 0.0 S-MH-3403 A28 10.1 0.0 9.1 0.0 S-MH-3430 A28 20.2 0.0 18.2 0.0 S-MH-3443 A4 19.3 1.4 13.5 0.0 S-MH-357 A5 27.1 0.9 17.3 0.0 S-MH-277 A6 27.3 3.0 18.3 0.0 MH-22 A6 28.6 3.0 18.3 0.0 S-MH-3768 A6 27.3 0.0 18.3 0.0 S-MH-1548 A7 19.8 0.0 25.9 0.0 S-MH-1455 A7 14.2 0.4 0.0 0.0 S-MH-1494 A8 18.6 6.3 18.5 0.0 S-MH-1795 A9 11.9 15.8 19.9 0.0 S-MH-2333 B1 22.8 9.3 15.0 0.0 S-MH-750 B1 22.3 9.3 15.0 0.0 S-MH-800 (1) Residential flows shown are prior to peaking. All residential flow was peaked within the model.P.1 M:\Marysville\11447\Modeling\ Flows\Node input 2031 for modela 2700 gpad w planning areas Aug.xls Marysville Sewer Comprehensive Plan Buildout Model Input Sub-Basin Load 1: Residential Input1 (gpm) Load 2: Commercial Input (gpm) Load 3: I/I Input (gpm) Load 4: Fixed Flow (gpm) Input Node B2 17.9 0.0 0.0 0.0 S-MH-795 B3 19.5 12.3 13.7 0.0 S-MH-789 B4 11.5 0.0 1.9 0.0 S-MH-1648 B5 15.1 0.0 1.7 0.0 MH-216 CE1 9.6 0.0 8.7 0.0 S-MH-1522 CE2 22.4 0.4 12.4 0.0 S-MH-1751 CE3 15.9 0.0 18.9 0.0 S-MH-1745 CE4 9.7 0.0 13.3 0.0 S-MH-1743 CE5 16.3 0.0 0.0 0.0 S-MH-1753 CE5 7.2 0.0 32.9 0.0 S-MH-1688 CE5-1 14.1 0.0 14.1 0.0 S-MH-1679 CE5-1 3.9 0.0 14.4 0.0 S-MH-1671 CE5-2 10.3 186.3 62.2 0.0 S-MH-1657 CE5-3 29.2 0.0 44.9 0.0 S-MH-1964 CE5-3(Future)45.5 0.0 205.6 0.0 S-MH-2055 CE5-4 4.5 13.2 11.9 0.0 S-MH-3757 CE5-5 6.7 0.0 8.6 0.0 S-MH-1973 CE5-6 9.4 0.0 13.4 0.0 S-MH-1943 CE5-7 140.2 101.5 89.5 0.0 S-MH-4642 CE6 25.8 0.0 27.7 0.0 S-MH-2074 CE7 31.7 0.0 38.1 0.0 S-MH-2117 CE8 14.7 0.0 15.2 0.0 S-MH-2062 CE9 14.0 1.9 17.7 0.0 S-MH-2281 CW1 32.7 90.0 61.5 0.0 S-MH-3577 CW1 33.0 0.0 30.8 0.0 S-MH-483 CW10 26.5 9.5 24.4 0.0 S-MH-1513 CW11 20.9 29.3 16.9 17.6 S-MH-1765 CW11-1 43.7 0.0 15.4 0.0 S-MH-1775 CW11-1 43.7 52.7 15.4 0.0 S-MH-4716 CW12 9.4 44.8 26.7 0.0 S-MH-1537 CW13 14.3 62.5 29.1 9.1 S-MH-1800 CW14 21.2 16.3 10.0 0.0 S-MH-1852 CW14 8.8 16.3 10.0 0.0 S-MH-1849 CW15 62.2 18.0 3.8 0.0 S-MH-1834 CW15 62.2 0.0 3.8 0.0 S-MH-4377 CW2 6.5 11.1 9.3 0.0 S-MH-481 CW2 13.1 11.1 18.8 0.0 S-MH-477 CW3 58.2 16.9 56.5 11.5 S-MH-308 CW4 19.8 64.3 34.0 0.0 S-MH-449 CW5 0.8 48.4 18.7 11.3 S-MH-4089 CW6 34.7 6.9 21.6 0.0 S-MH-1369 CW7 15.6 87.5 42.4 0.0 S-MH-246 CW8 15.3 0.0 19.0 0.0 S-MH-1564 CW8 15.3 47.7 19.0 0.0 S-MH-1567 CW9 0.1 46.0 20.0 0.0 S-MH-1568 D1 5.4 7.7 18.1 0.0 S-MH-533 D10 11.4 0.0 18.0 0.0 S-MH-2007 D10-1 33.0 43.1 0.0 0.0 S-MH-3916 D10-2 66.3 123.8 20.4 0.0 S-MH-4192 D10-3 36.2 0.0 0.0 0.0 S-MH-4546 D10-4 29.7 0.0 0.0 0.0 S-MH-4864 D10-5 12.3 20.6 0.0 0.0 S-MH-905 D10-6 62.0 0.0 22.8 0.0 S-MH-4545 D11 8.7 0.0 18.9 0.0 S-MH-1924 D12 28.9 0.0 49.3 0.0 S-MH-3732 D2 6.7 0.0 8.3 0.0 S-MH-624 D3 13.2 10.7 24.5 0.0 S-MH-641 D3-1 11.5 0.0 18.6 0.0 S-MH-1305 D3-1 11.5 0.0 18.6 0.0 S-MH-635 D3-10 18.4 0.0 20.8 0.0 S-MH-40 D3-10 18.4 0.0 20.8 0.0 S-MH-975 D3-11 55.9 0.0 61.0 0.0 S-MH-4872 D3-12 95.6 0.0 79.5 0.0 S-MH-110 D3-13 22.1 0.0 16.6 0.0 S-MH-1318 D3-2 16.3 0.0 16.9 0.0 S-MH-1209 D3-3 17.9 0.0 21.8 0.0 S-MH-1216 D3-4 27.9 0.0 14.7 0.0 S-MH-3697 D3-5 33.4 3.3 26.7 0.0 S-MH-3382 D3-5 50.1 1.6 40.0 0.0 S-MH-3357 D3-5 27.8 1.6 22.2 0.0 S-MH-3381 D3-6 15.3 2.8 15.1 0.0 S-MH-3309 D3-7 21.3 0.0 18.4 0.0 S-MH-3294 D3-8 27.4 0.0 25.8 0.0 MH-162 D3-8 27.4 0.0 25.8 0.0 S-MH-3672 D3-9 17.5 0.0 22.2 0.0 S-MH-3677 D3-9 17.5 0.0 22.2 0.0 S-MH-3705 D4 16.9 0.0 21.6 0.0 S-MH-844 (1) Residential flows shown are prior to peaking. All residential flow was peaked within the model.P.2 M:\Marysville\11447\Modeling\ Flows\Node input 2031 for modela 2700 gpad w planning areas Aug.xls Marysville Sewer Comprehensive Plan Buildout Model Input Sub-Basin Load 1: Residential Input1 (gpm) Load 2: Commercial Input (gpm) Load 3: I/I Input (gpm) Load 4: Fixed Flow (gpm) Input Node D5 23.3 6.2 32.9 0.0 S-MH-669 D5-1 6.6 11.4 14.6 10.0 S-MH-852 D5-2 19.1 11.5 21.8 0.0 S-MH-853 D5-2 19.2 0.0 21.8 0.0 S-MH-916 D6 27.0 0.0 42.4 0.0 S-MH-706 D6-1 10.8 0.0 14.9 0.0 S-MH-717 D6-2 100.9 6.0 133.7 0.0 S-MH-906 D6-3 12.0 0.0 21.1 0.0 S-MH-898 D6-4 18.8 0.0 25.7 0.0 S-MH-1006 D6-5 57.9 37.5 34.6 0.0 S-MH-1071 D7 6.3 0.0 13.1 0.0 S-MH-1609 D7-1 15.8 0.0 10.2 0.0 S-MH-1591 D7-2 17.3 0.0 17.3 0.0 S-MH-1593 D8 6.5 5.2 15.8 0.0 S-MH-2001 D9 19.1 0.0 36.8 0.0 S-MH-924 D9-1 17.6 0.0 19.4 0.0 S-MH-1169 F1 5.4 0.0 2.0 0.0 S-MH-2362 F10 0.1 29.3 27.9 0.0 S-MH-2705 F10 0.0 117.2 13.8 0.0 MH-102 F11 0.1 54.9 20.6 0.0 S-MH-2589 F12 0.4 99.8 21.5 0.0 S-MH-2719 F12 0.4 99.8 21.5 0.0 S-MH-2596 F13 0.1 132.9 35.4 0.0 S-MH-3462 F13(Future)887.7 0.0 897.1 0.0 S-MH-4581 F13(Future)295.9 0.0 299.0 0.0 S-MH-4575 F13-1 8.6 113.4 18.7 0.0 S-MH-4564 F13-1 8.6 113.4 18.7 0.0 S-MH-4568 F13-2 6.4 123.8 16.5 0.0 S-MH-4576 F14 1.4 79.8 12.1 83.9 S-MH-3847 F14 1.0 0.0 12.2 0.0 S-MH-3845 F14 1.0 79.8 12.2 0.0 S-MH-3467 F15 3.3 48.1 12.9 0.0 S-MH-3470 F15 3.4 48.1 12.9 0.0 S-MH-3044 F15 3.6 24.1 12.8 0.0 S-MH-3638 F16 0.3 47.8 10.5 0.0 S-MH-3527 F16 0.3 47.8 10.5 0.0 S-MH-3525 F17 0.8 38.3 9.3 0.0 S-MH-3531 F17 0.7 38.3 9.3 0.0 S-MH-3533 F18 0.0 35.9 11.0 0.0 S-MH-3538 F18 0.0 35.9 11.0 0.0 S-MH-3109 F19 0.0 36.4 14.6 0.0 S-MH-3536 F19 0.0 54.6 14.6 9.0 S-MH-3498 F2 14.6 0.0 2.6 0.0 S-MH-2363 F20 10.5 140.1 35.0 0.0 S-MH-3506 F20 34.9 0.0 29.1 0.0 S-MH-3510 F21 72.7 37.1 39.5 0.0 S-MH-3205 F22 11.9 0.0 13.4 0.0 S-MH-3155 F22 11.9 57.0 13.5 0.0 S-MH-3148 F22 11.9 0.0 13.5 0.0 S-MH-4910 F22(Future)1,178.8 0.0 1,191.1 0.0 S-MH-4569 F22-1 51.0 197.4 74.9 0.0 S-MH-3239 F3 9.6 0.0 21.8 0.0 S-MH-2364 F4 37.2 0.0 43.6 0.0 S-MH-2708 F5 22.5 44.2 26.6 0.0 S-MH-2357 F5 5.6 44.2 6.7 0.0 S-MH-2356 F6 5.3 0.0 7.3 0.0 S-MH-3860 F7 8.9 54.5 19.3 0.0 MH-166 F8 5.6 34.7 12.5 0.0 S-MH-2760 F9 0.0 58.1 16.6 8.2 S-MH-2684 G1 29.6 69.4 55.7 0.0 S-MH-428 G2 29.3 21.4 18.1 0.0 S-MH-420 G2 29.3 0.0 18.1 0.0 S-MH-464 G3 0.1 144.2 41.5 0.0 S-MH-2476 G4 1.2 51.5 19.2 0.0 S-MH-2540 G5 17.1 0.0 24.9 0.0 S-MH-2482 G6 15.4 0.0 21.3 0.0 S-MH-2509 G7 26.1 54.0 6.0 0.0 S-MH-2548 G8 2.8 19.7 9.0 0.0 S-MH-2550 Totals:6,635 5,600 8,662 198 (1) Residential flows shown are prior to peaking. All residential flow was peaked within the model.P.3 M:\Marysville\11447\Modeling\ Flows\Node input 2031 for modela 2700 gpad w planning areas Aug.xls APPENDIX E HYDRAULIC MODEL RESULTS " " " " " " " !( !( !( !( !(!(!(!( !(!(!( !( !( !( !(!( !( !( !(!(!(!(!( !( !( !( !(!(!(!(!(!(!(!( !( !( !( !( !( !( !( !( !( !( !( !( !(!( !( !( !( !( !( !( !(!(!(!( !( !(!(!(!( !(!( !(!( !( !(!(!( !( !( !( !( !(!(!(!( !(!( !( !( !( !( !( !(!( !(!( !(!(!(!( !( !( !( !( !(!( !( !( !( !( !( !( !(!( !( !( !(!( !( !( !( !( !(!( !( !(!( !( !( !(!(!(!(!(!(!(!(!(!( !(!(!( !( !( !( !( !( !(!(!( !( !(!(!( !(!(!(!(!(!(!( !( !( !( !( !( !(!(!( !( !( !(!(!(!(!(!(!(!(!(!( !( !( !( !( !( !(!(!(!(!(!(!(!(!( !( !(!(!(!( !( !(!( !( !(!(!(!(!(!( !(!(!( !(!(!(!( !(!(!(!(!(!(!( !( !( !( !( !(!(!(!( !( !( !( !( !( !( !(!(!(!(!( !(!( !(!(!(!( !(!( !(!( !(!( !( !( !( !( !(!(!(!( !(!( !(!( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !( !( !( !( !(!(!(!(!(!(!(!(!(!(!(!(!(!( !(!(!(!(!(!(!(!( !( !( !( !(!(!(!(!(!( !(!(!( !( !(!(!(!(!(!( !( !(!(!(!(!(!(!(!(!( !(!( !( !( !(!( !(!(!( !(!(!(!(!(!(!(!( !(!(!(!(!(!(!(!(!( !( !( !( !( !( !( !(!(!( !( !(!( !( !(!( !( !( !( !( !(!(!( !(!(!(!(!(!( !(!( !( !(!(!( !( !(!(!( !( !(!( !( !( !( !(!(!( !(!( !(!(!(!(!(!( !( !( !(!(!(!(!(!(!( !( !(!( !( !(!( !(!(!(!(!(!(!(!( !( !( !(!(!(!(!(!(!(!(!(!(!(!(!(!( !(!(!( !(!(!( !( !(!(!( !(!( !(!( !(!( !(!(!(!(!( !( !( !( !(!( !(!(!(!(!(!( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !(!( !( !(!(!(!(!(!( !( !( !( !(!(!( !( !(!(!(!(!( !( !(!(!(!(!(!(!(!(!( !( !( !( !( !(!(!(!(!(!( !( !( !( !(!( !( !( !( !(!(!( !( !( !(!(!(!( !( !( !(!( !(!( !( !(!( !(!( !( !(!(!( !(!( !(!( !( !(!( !( !( !(!(!(!(!(!(!(!( !( !( !( !(!( !( !(!(!( !( !( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !( !(!( !( !( !( !( !(!( !(!(!(!(!(!(!(!(!(!( !( !( !( !( !( !( !(!( !(!(!(!(!( !(!(!(!( !(!( !( !(!(!( !( !(!(!(!(!( !( !(!( !(!( !(!(!( !(!(!( !( !( !( !(!( !( !( !( !( !(!(!( !( !(!(!(!(!(!(!( !(!(!(!( !(!(!(!(!(!( !( !(!(!(!(!(!( !( !(!(!(!(!(!(!( !(!(!( !( !( !(!(!(!(!(!(!(!(!(!( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !(!( !(!( !(!( !(!( !( !( !(!(!( !(!(!(!(!( !( !( !( !(!(!( !( !( !( !( !( !( !(!( !(!(!(!(!(!(!(!(!(!( !( !(!( !( !(!( !( !(!( !( !( !(!( !( !( !(!(!( !( !( !( !( !( !(!(!(!(!(!(!(!(!( !(!(!( !( !( !( !( !(!(!(!(!(!(!(!( !( !( !(!( !(!( !(!( !( !( !( !( !(!(!(!(!(!(!(!(!( !( !(!(!( !(!( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !( !( !( !( !(!( !(!(!(!(!(!( !(!(!(!(!(!( !(!(!(!( !( !(!( !(!( !( !(!( !(!(!( !( !( !( !( !( !( !( !( !( !( !(!(!(!(!(!(!( !( !( !( !( !( !( !( !(!(!(!(!( !( !(!( !( !( !(!( !(!( !( !( !(!(!(!(!(!(!( !( !( !( !( !(!(!(!(!( !( !( !( !( !( !(!(!(!( !( !(!(!(!(!(!(!(!( !(!(!(!( !(!( !( !( !(!(!(!( !( !(!(!( !( !( !( !( !( !( !( !(!( !(!( !( !( !( !( !( !(!(!(!(!(!(!(!(!( !(!(!(!(!(!(!( !( !(!( !(!(!( !( !(!( !(!(!(!(!( !(!(!( !( !(!( !(!(!(!(!(!( !(!( !( !(!(!(!(!(!(!(!(!(!( !(!(!(!(!(!( !(!(!( !(!( !(!(!(!( !(!(!(!(!( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !(!( !( !( !( !(!(!( !(!( !(!( !( !( !( !( !( !(!(!(!( !(!(!(!( !(!(!( !(!( !( !( !( !( !( !( !( !( !( !( !(!( !( !( !( !( !(!( !( !( !(!( !( !(!( !( !( !(!(!(!( !(!( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !(!(!(!( !( !( !( !( !( !( !(!( !( !( !(!(!(!(!(!(!(!( !( !(!(!(!(!(!(!(!( !(!(!( !( !(I-5SR-9CE5-7 G7 CW1 D3-5 D6-2 CW15 F22-1 A6 G3 F13-1 B1 D3-12 A25-1 A19 D10-2 G1 D10-6 A24-5 CW11-1 F4 D6-5 A21 F20 A26 F12 D1 F22 F21 D10-3 F14 A20 A23 A10 A16 D10-4 A7 D3-11 G2 F5 D6 A15 G4 G8 A13 A25 A22 D10-1 F15 D3-8 D9 F13 F10 B2 D12 D3 D5 A24 A18 CW3 A28 F7 D3-1 F13-2 A27 A24-4 A8 A17 CW11 CE5-2 A5 D3-4 A24-2 A24-3 D3-10 B3 D3-9 D5-2 CE5 CE7 CE6 G5 CW7 D3-6 F16 A12 F2 D3-13 CW2 F3 F17 CW14 F9 A24-1 CW8 D3-3 B5 G6 F19 D4 D6-4 CE5-3CE2 CW12 A2 CW10 A16-1 A9 CW4 F8 A12-2 D3-7 D3-2 D2 D10-5 A4 F18 F11 CE3 B4 D8 D9-1 D10 A1 A18-1 CE5-1 A11 A12-3 D5-1 D11 CW13 D7 A14 CE9 D6-3 A18-3 CE5-4 CW9 D7-2 CW5 F1 D6-1 CE1 F6 D7-1 CE5-6 CW6 A12-4 CE8 CE4 A12-1 A18-2 CE5-5 CITY OF MARYSVILLE SEWER COMPREHENSIVE PLAN FIGURE 7-4 MODEL RESULTS (2011) M:\MARYSVILLE\11447_Sewer_Comp_Plan\Figures\Fig 7-4 Model Results 2011.mxd Legend !(Modeled Manhole !(Surcharged Manhole (<0.5') !(Surcharged Manhole (>0.5') "Modeled Pump Station Modeled Force Main Sanitary Sewer Pipe Deficient Sewer Pipe Subbasin Parcel ³ 0 3,600 7,2001,800 Feet Note: Pipeline identification labels are shown on Exhibit IV and surcharge results may be found in Appendix G. Marysville Sewer Comprehensive Plan 2011 Modeled Pipe Deficiencies City Pipe Number Diameter (inches) Length (Ft)Material Slope (ft/ft) Upstream Manhole Downstream Manhole Upstream Invert (ft) Downstream Invert (ft) Peakable (Residential) Flow (gpm) Unpeakable (Commercial / I&I) Flow (gpm) Total Flow (gpm) Design Capacity (gpm) Modeled Flow to Design Flow Ratio Velocity (ft/s) Upstream Surcharge Depth (ft) S-LINE-1010 15 360 Concrete 0.0000 S-MH-708 S-MH-706 48.61 48.61 130.3 190.5 634.9 91.9 6.91 1.15 0.17 S-LINE-1011 15 102 Concrete 0.0000 S-MH-704 S-MH-703 47.09 47.09 156.7 229.3 751.3 91.9 8.17 1.36 0.07 S-LINE-11994 15 333 PVC 0.0040 S-MH-6727 S-MH-3546 12.09 10.80 43.3 1,863.0 2,020.8 1,809.4 1.12 3.67 3.05 S-LINE-11995 15 157 PVC 0.0040 S-MH-3546 S-MH-3547 10.70 10.12 43.3 1,863.0 2,020.8 1,766.9 1.14 3.67 2.83 S-LINE-11996 15 353 PVC 0.0020 S-MH-3547 S-MH-3548 10.02 9.48 43.3 1,863.0 2,020.8 1,137.0 1.78 3.67 2.74 S-LINE-1462 24 374 Unknown 0.0000 S-MH-3608 S-MH-3802 24.67 24.57 236.6 1,212.4 1,958.7 1,680.5 1.17 1.39 0.04 S-LINE-2097 12 338 PVC 0.0010 S-MH-1606 S-MH-1605 51.61 51.23 130.3 190.5 634.9 537.6 1.18 1.80 0.15 S-LINE-2099 12 36 PVC 0.0010 S-MH-900 S-MH-857 51.80 51.78 89.3 153.6 468.0 377.9 1.24 1.33 0.15 S-LINE-2185 18 389 Concrete 0.0010 S-MH-1746 S-MH-1748 51.06 50.75 251.7 622.7 1,410.8 1,334.5 1.06 1.78 0.04 S-LINE-2197 12 100 PVC 0.0010 S-MH-1754 S-MH-1755 55.30 55.14 133.7 449.9 905.1 614.3 1.47 2.57 0.19 S-LINE-2198 12 203 DI 0.0020 S-MH-1753 S-MH-1754 55.80 55.30 133.7 449.9 905.1 795.7 1.14 2.57 0.34 S-LINE-2199 12 242 DI 0.0030 S-MH-1651 S-MH-1753 56.45 55.80 125.4 449.9 878.8 830.9 1.06 2.49 0.42 S-LINE-2203 12 407 DI 0.0030 S-MH-1657 S-MH-1651 57.50 56.45 125.4 449.9 878.8 814.4 1.08 2.49 0.60 S-LINE-2214 12 98 PVC 0.0010 S-MH-2034 S-MH-1661 62.01 61.94 114.6 182.0 576.6 428.5 1.35 1.64 0.06 S-LINE-2544 12 133 Unknown 0.0000 S-MH-1998 S-MH-1999 63.13 63.08 114.6 182.0 576.6 310.9 1.86 1.64 0.12 S-LINE-475 48 74 Clay 0.0000 S-MH-540 S-MH-541 20.94 20.94 707.4 6,190.9 8,139.0 2,044.3 3.98 1.44 0.01 S-LINE-5004 12 220 PVC 0.0010 S-MH-4594 S-MH-4596 110.05 109.81 81.1 265.7 554.1 544.6 1.02 1.57 0.01 S-LINE-5005 12 273 PVC 0.0000 S-MH-3506 S-MH-4594 110.15 110.05 81.1 265.7 554.1 301.4 1.84 1.57 0.25 S-LINE-510 18 258 Unknown 0.0010 S-MH-379 S-MH-4089 26.98 26.75 89.4 1,274.0 1,588.7 1,411.4 1.13 2.00 0.06 S-LINE-5113 21 372 Unknown 0.0020 S-MH-3574 S-MH-3575 6.26 5.44 294.2 3,623.8 4,527.3 3,347.9 1.35 4.19 0.69 S-LINE-5116 24 58 Unknown 0.0010 S-MH-3591 S-MH-3870 3.43 3.36 294.2 3,623.8 4,527.3 3,477.4 1.30 3.21 0.49 S-LINE-5117 24 395 Unknown 0.0010 S-MH-3870 S-MH-3594 3.36 3.01 294.2 3,623.8 4,527.3 3,030.5 1.49 3.21 0.44 S-LINE-5119 21 75 Unknown 0.0040 S-MH-3585 S-MH-3574 6.61 6.36 294.2 3,623.8 4,527.3 4,231.3 1.07 4.19 0.63 S-LINE-5218 15 417 Unknown 0.0000 S-MH-3581 S-MH-3582 8.81 8.78 43.3 1,863.0 2,020.8 246.6 8.20 3.67 2.10 S-LINE-624 18 315 Unknown 0.0020 S-MH-4862 S-MH-327 12.22 11.53 199.8 1,588.7 2,232.5 2,161.6 1.03 2.82 0.05 S-LINE-6493 30 24 PVC 0.0000 S-MH-4552 S-MH-4551 93.28 93.28 81.1 300.9 589.3 583.7 1.01 0.27 0.00 S-LINE-661 21 307 Concrete 0.0000 MH-13 S-MH-432 13.44 13.30 0.1 1,710.3 1,710.6 1,522.7 1.12 1.59 1.77 S-LINE-664 21 319 Unknown 0.0000 S-MH-328 S-MH-469 11.83 11.81 0.1 1,710.3 1,710.6 568.2 3.01 1.59 3.09 S-LINE-675 24 368 Concrete 0.0010 S-MH-651 S-MH-624 21.77 21.57 666.7 1,848.4 3,698.7 2,373.4 1.56 2.62 0.29 S-LINE-703 21 259 Concrete 0.0000 S-MH-591 S-MH-597 40.83 40.80 349.4 480.5 1,528.9 767.4 1.99 1.42 0.09 S-LINE-711 18 252 Concrete 0.0010 S-MH-670 S-MH-671 43.09 42.84 349.4 480.5 1,528.9 1,488.9 1.03 1.93 0.02 S-LINE-712 18 123 Concrete 0.0000 S-MH-669 S-MH-670 43.16 43.16 349.4 480.5 1,528.9 149.5 10.23 1.93 0.13 S-LINE-717 18 423 Concrete 0.0010 S-MH-700 S-MH-697 45.62 45.28 326.5 444.2 1,432.4 1,340.2 1.07 1.81 0.05 S-LINE-731 12 289 PVC 0.0020 S-MH-717 S-MH-702 47.24 46.76 169.8 214.9 773.9 653.4 1.18 2.20 0.20 S-LINE-852 12 219 PVC 0.0020 S-MH-733 S-MH-717 47.61 47.24 158.8 200.0 728.0 659.0 1.11 2.07 0.28 M:\MARYSVILLE\11447_Sewer_Comp_Plan\Appendices\Appx G pipe_deficiencies_2011.xls " " " " " " " !( !( !( !( !(!(!(!( !(!(!( !( !( !( !(!( !( !( !(!(!(!(!( !( !( !( !(!(!(!(!(!(!(!( !( !( !( !( !( !( !( !( !( !( !( !( !(!( !( !( !( !( !( !( !(!(!(!( !( !(!(!(!( !(!( !(!( !( !(!(!( !( !( !( !( !(!(!(!( !( !( !( !( !( !(!( !(!( !(!(!(!( !( !( !( !( !(!( !( !( !( !( !( !( !(!( !( !( !(!( !( !( !( !( !(!( !( !(!( !( !( !(!(!(!(!(!(!(!(!(!( !(!(!( !( !( !( !( !( !(!(!( !( !(!(!( !(!(!(!(!(!(!( !( !( !( !( !( !(!(!( !( !( !(!(!(!(!(!(!(!(!(!( !( !( !( !( !( !(!(!(!(!(!(!(!(!( !( !(!(!(!( !( !(!( !( !(!(!(!(!(!( !(!(!( !(!(!(!( !(!(!(!(!(!(!( !( !( !( !( !(!(!(!( !( !( !( !( !( !( !(!(!(!(!(!(!( !(!(!(!( !(!( !(!( !(!( !( !( !( !( !(!(!(!( !(!( !(!( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !( !( !( !( !(!(!(!(!(!(!(!(!(!(!(!(!(!( !(!(!(!(!(!(!(!( !( !( !( !(!(!(!(!(!( !(!(!( !( !(!(!(!(!(!( !( !(!(!(!(!(!(!(!(!( !(!( !( !( !(!( !(!(!( !(!(!(!(!(!(!(!( !(!(!(!(!(!(!(!(!( !( !( !( !( !( !( !(!(!( !( !(!( !( !(!( !( !( !( !( !(!(!( !(!(!(!(!(!( !(!( !( !(!(!( !( !(!(!( !( !(!( !( !( !( !(!(!( !(!( !(!(!(!(!(!( !( !( !(!(!(!(!(!(!( !( !(!( !( !(!( !(!(!(!(!(!(!(!( !( !( !(!(!(!(!(!(!(!(!(!(!(!(!(!( !(!(!( !(!(!( !( !(!(!( !(!( !(!( !(!( !(!(!(!(!( !( !( !( !(!( !(!(!(!(!(!( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !(!( !( !(!(!(!(!(!( !( !( !( !(!(!( !( !(!(!(!(!( !( !(!(!(!(!(!(!(!(!( !( !( !( !( !(!(!(!(!(!( !( !( !( !(!( !( !( !( !(!(!( !( !( !(!(!(!( !( !( !(!( !(!( !( !(!( !(!( !( !(!(!( !(!( !(!( !( !(!( !( !( !(!(!(!(!(!(!(!( !( !( !( !(!( !( !(!(!( !( !( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !( !(!( !( !( !( !( !(!( !(!(!(!(!(!(!(!(!(!( !( !( !( !( !( !( !(!( !(!(!(!(!( !(!(!(!( !(!( !( !(!(!( !( !(!(!(!(!( !( !(!( !(!( !(!(!( !(!(!( !( !( !( !(!( !( !( !( !( !(!(!( !( !(!(!(!(!(!(!( !(!(!(!( !(!(!(!(!(!( !( !(!(!(!(!(!( !( !(!(!(!(!(!(!( !(!(!( !( !( !(!(!(!(!(!(!(!(!(!( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !(!( !(!( !(!( !(!( !( !( !(!(!( !(!(!(!(!( !( !( !( !(!(!( !( !( !( !( !( !( !(!( !(!(!(!(!(!(!(!(!(!( !( !(!( !( !(!( !( !(!( !( !( !(!( !( !( !(!(!( !( !( !( !( !( !(!(!(!(!(!(!(!(!( !(!(!( !( !( !( !( !(!(!(!(!(!(!(!( !( !( !(!( !(!( !(!( !( !( !( !( !(!(!(!(!(!(!(!(!( !( !(!(!( !(!( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !( !( !( !( !(!( !(!(!(!(!(!( !(!(!(!(!(!( !(!(!(!( !( !(!( !(!( !( !(!( !(!(!( !( !( !( !( !( !( !( !( !( !( !(!(!(!(!(!(!( !( !( !( !( !( !( !( !(!(!(!(!( !( !(!( !( !( !(!( !(!( !( !( !(!(!(!(!(!(!( !( !( !( !( !(!(!(!(!( !( !( !( !( !( !(!(!(!( !( !(!(!(!(!(!(!(!( !(!(!(!( !(!( !( !( !(!(!(!( !( !(!(!( !( !( !( !( !( !( !( !(!( !(!( !( !( !( !( !( !(!(!(!(!(!(!(!(!( !(!(!(!(!(!(!( !( !(!( !(!(!( !( !(!( !(!(!(!(!( !(!(!( !( !(!( !(!(!(!(!(!( !(!( !( !(!(!(!(!(!(!(!(!(!( !(!(!(!(!(!( !(!(!( !(!( !(!(!(!( !(!(!(!(!( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !(!( !( !( !( !(!(!( !(!( !(!( !( !( !( !( !( !(!(!(!( !(!(!(!( !(!(!( !(!( !( !( !( !( !( !( !( !( !( !( !(!( !( !( !( !( !(!( !( !( !(!( !( !(!( !( !( !(!(!(!( !(!( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !(!(!(!( !( !( !( !( !( !( !(!( !( !( !(!(!(!(!(!(!(!( !( !(!(!(!(!(!(!(!( !(!(!( !( !(I-5SR-9CE5-7 G7 CW1 D3-5 D6-2 CW15 F22-1 A6 G3 F13-1 B1 D3-12 A25-1 A19 D10-2 G1 D10-6 A24-5 CW11-1 F4 D6-5 A21 F20 A26 F12 D1 F22 F21 D10-3 F14 A20 A23 A10 A16 D10-4 A7 D3-11 G2 F5 D6 A15 G4 G8 A13 A25 A22 D10-1 F15 D3-8 D9 F13 F10 B2 D12 D3 D5 A24 A18 CW3 A28 F7 D3-1 F13-2 A27 A24-4 A8 A17 CW11 CE5-2 A5 D3-4 A24-2 A24-3 D3-10 B3 D3-9 D5-2 CE5 CE7 CE6 G5 CW7 D3-6 F16 A12 F2 D3-13 CW2 F3 F17 CW14 F9 A24-1 CW8 D3-3 B5 G6 F19 D4 D6-4 CE5-3CE2 CW12 A2 CW10 A16-1 A9 CW4 F8 A12-2 D3-7 D3-2 D2 D10-5 A4 F18 F11 CE3 B4 D8 D9-1 D10 A1 A18-1 CE5-1 A11 A12-3 D5-1 D11 CW13 D7 A14 CE9 D6-3 A18-3 CE5-4 CW9 D7-2 CW5 F1 D6-1 CE1 F6 D7-1 CE5-6 CW6 A12-4 CE8 CE4 A12-1 A18-2 CE5-5 CITY OF MARYSVILLE SEWER COMPREHENSIVE PLAN FIGURE 7-5 MODEL RESULTS (2017) M:\MARYSVILLE\11447_Sewer_Comp_Plan\Figures\Fig 7-5 Model Results 2017.mxd Legend !(Modeled Manhole !(Surcharged Manhole (<0.5') !(Surcharged Manhole (>0.5') "Modeled Pump Station Modeled Force Main Sanitary Sewer Pipe Deficient Sewer Pipe Subbasin Parcel ³ 0 3,500 7,0001,750 Feet Note: Pipeline identification labels are shown on Exhibit IV and surcharge results may be found in Appendix G. Marysville Sewer Comprehensive Plan 2017 Modeled Pipe Deficiencies City Pipe Number Diameter (inches) Length (Ft)Material Slope (ft/ft) Upstream Manhole Downstream Manhole Upstream Invert (ft) Downstream Invert (ft) Peakable (Residential) Flow (gpm) Unpeakable (Commercial / I&I) Flow (gpm) Total Flow (gpm) Design Capacity (gpm) Modeled Flow to Design Flow Ratio Velocity (ft/s) Upstream Surcharge Depth (ft) S-LINE-1010 15 360 Concrete 0.0000 S-MH-708 S-MH-706 48.61 48.61 137.2 161.8 628.1 91.9 6.83 1.14 0.17 S-LINE-1011 15 101 Concrete 0.0000 S-MH-704 S-MH-703 47.09 47.09 165.3 194.6 740.9 91.9 8.06 1.35 0.07 S-LINE-11994 15 333 PVC 0.0040 S-MH-6727 S-MH-3546 12.09 10.80 54.0 1,871.5 2,067.7 1,809.4 1.14 3.75 3.38 S-LINE-11995 15 157 PVC 0.0040 S-MH-3546 S-MH-3547 10.70 10.12 54.0 1,871.5 2,067.7 1,766.9 1.17 3.75 3.07 S-LINE-11996 15 353 PVC 0.0020 S-MH-3547 S-MH-3548 10.02 9.48 54.0 1,871.5 2,067.7 1,137.0 1.82 3.75 2.95 S-LINE-1462 24 367 Unknown 0.0000 S-MH-3608 S-MH-3802 24.67 24.57 280.0 1,169.0 2,035.3 1,680.5 1.21 1.44 0.05 S-LINE-2097 12 338 PVC 0.0010 S-MH-1606 S-MH-1605 51.61 51.23 137.2 161.8 628.1 537.6 1.17 1.78 0.14 S-LINE-2099 12 36 PVC 0.0010 S-MH-900 S-MH-857 51.80 51.78 96.0 130.7 466.3 377.9 1.23 1.32 0.13 S-LINE-2185 18 389 Concrete 0.0010 S-MH-1746 S-MH-1748 51.06 50.75 281.9 638.0 1,509.2 1,334.5 1.13 1.90 0.09 S-LINE-2195 12 58 PVC 0.0040 S-MH-1755 S-MH-4607 55.14 54.92 152.6 490.0 1,000.4 987.5 1.01 2.84 0.01 S-LINE-2197 12 109 PVC 0.0010 S-MH-1754 S-MH-1755 55.30 55.14 152.6 490.0 1,000.4 614.3 1.63 2.84 0.27 S-LINE-2198 12 203 DI 0.0020 S-MH-1753 S-MH-1754 55.80 55.30 152.6 490.0 1,000.4 795.7 1.26 2.84 0.57 S-LINE-2199 12 242 DI 0.0030 S-MH-1651 S-MH-1753 56.45 55.80 141.5 490.0 969.1 830.9 1.17 2.75 0.81 S-LINE-2203 12 407 DI 0.0030 S-MH-1657 S-MH-1651 57.50 56.45 141.5 490.0 969.1 814.4 1.19 2.75 1.25 S-LINE-2214 12 98 PVC 0.0010 S-MH-2034 S-MH-1661 62.01 61.94 130.7 241.5 687.2 428.5 1.60 1.95 0.11 S-LINE-2371 8 219 PVC 0.0000 S-MH-3769 S-MH-1422 45.74 45.67 24.3 16.8 106.2 97.2 1.09 0.68 0.01 S-LINE-2488 15 161 PVC 0.0000 S-MH-1834 S-MH-1838 47.90 47.89 47.2 88.1 259.9 229.1 1.14 0.47 0.00 S-LINE-2544 12 133 Unknown 0.0000 S-MH-1998 S-MH-1999 63.13 63.08 130.7 241.5 687.2 310.9 2.21 1.95 0.20 S-LINE-3188 21 420 Concrete 0.0020 S-MH-2362 S-MH-2384 63.13 62.48 193.4 2,507.9 3,133.6 2,805.2 1.12 2.90 0.17 S-LINE-3191 21 347 Concrete 0.0020 S-MH-2363 S-MH-2362 63.72 63.13 191.3 2,506.4 3,126.2 2,940.3 1.06 2.90 0.25 S-LINE-3200 21 407 Concrete 0.0010 MH-221 S-MH-2383 68.72 68.20 128.7 2,337.4 2,776.7 2,548.8 1.09 2.57 0.11 S-LINE-3201 21 14 Concrete 0.0010 S-MH-2383 S-MH-2382 68.20 68.18 142.7 2,450.8 2,933.3 2,695.1 1.09 2.72 0.00 S-LINE-3295 21 466 Concrete 0.0020 S-MH-3792 S-MH-3793 66.89 66.07 175.4 2,483.6 3,058.5 2,991.2 1.02 2.83 0.04 S-LINE-3300 21 264 Concrete 0.0010 S-MH-3861 S-MH-3860 69.84 69.51 123.1 2,331.5 2,753.1 2,521.1 1.09 2.55 0.07 S-LINE-3586 18 497 Concrete 0.0020 S-MH-2757 MH-102 80.08 79.03 117.8 1,963.7 2,368.5 2,172.8 1.09 2.99 0.21 S-LINE-3588 18 479 Concrete 0.0010 S-MH-2701 S-MH-2761 76.69 76.00 117.8 2,141.6 2,546.4 1,794.2 1.42 3.21 0.96 S-LINE-3589 18 467 Concrete 0.0020 S-MH-2761 S-MH-2684 76.00 74.89 117.8 2,141.6 2,546.4 2,304.7 1.11 3.21 0.25 S-LINE-3597 18 369 Concrete 0.0030 S-MH-2760 S-MH-2759 73.67 72.64 119.4 2,262.5 2,672.3 2,497.5 1.07 3.37 0.16 S-LINE-3604 18 360 Concrete 0.0030 MH-1422 MH-166 71.43 70.33 119.4 2,262.5 2,672.3 2,613.1 1.02 3.37 0.06 S-LINE-3833 18 481 Concrete 0.0020 S-MH-2589 S-MH-2757 80.90 80.08 117.8 1,963.7 2,368.5 1,951.8 1.21 2.99 0.60 S-LINE-3881 12 233 Concrete 0.0000 MH-212 S-MH-2713 85.83 85.82 0.3 116.0 117.1 105.0 1.12 0.33 0.00 S-LINE-4246 30 178 Concrete 0.0000 S-MH-3025 S-MH-3024 83.10 83.08 174.8 2,118.3 2,691.5 1,956.7 1.38 1.22 0.02 S-LINE-4479 10 274 PVC 0.0010 S-MH-3203 S-MH-3204 112.20 111.96 65.1 66.8 302.8 291.8 1.04 1.24 1.68 S-LINE-4555 10 298 PVC 0.0010 S-MH-3242 S-MH-3241 112.73 112.55 5.0 253.8 272.2 242.3 1.12 1.11 1.19 S-LINE-475 48 74 Clay 0.0000 S-MH-540 S-MH-541 20.94 20.94 875.3 6,116.8 8,459.5 2,044.3 4.14 1.50 0.01 S-LINE-4849 14 331 Asbestos Cement 0.0000 S-MH-3424 S-MH-3425 112.45 112.36 25.3 309.9 403.0 398.8 1.01 0.84 0.00 S-LINE-5004 12 208 PVC 0.0010 S-MH-4594 S-MH-4596 110.05 109.81 97.5 508.9 849.3 544.6 1.56 2.41 0.35 S-LINE-5005 12 283 PVC 0.0000 S-MH-3506 S-MH-4594 110.15 110.05 97.5 508.9 849.3 301.4 2.82 2.41 1.05 S-LINE-5007 12 200 PVC 0.0010 S-MH-4595 S-MH-3506 110.40 110.20 91.2 342.5 662.9 507.0 1.31 1.88 1.14 S-LINE-5008 12 307 PVC 0.0010 S-MH-3510 S-MH-3505 110.81 110.55 91.2 342.5 662.9 466.6 1.42 1.88 1.45 S-LINE-5009 12 317 PVC 0.0010 S-MH-3521 S-MH-3510 111.16 110.85 70.1 320.6 574.1 501.4 1.15 1.63 1.51 S-LINE-5010 12 307 PVC 0.0010 S-MH-3513 S-MH-3521 111.52 111.18 70.1 320.6 574.1 533.6 1.08 1.63 1.55 S-LINE-5012 12 188 PVC 0.0010 S-MH-3522 S-MH-3513 111.86 111.64 70.1 320.6 574.1 548.5 1.05 1.63 1.45 S-LINE-5013 12 113 PVC 0.0010 S-MH-3204 S-MH-3522 111.96 111.86 70.1 320.6 574.1 477.0 1.20 1.63 1.49 S-LINE-510 18 258 Unknown 0.0010 S-MH-379 S-MH-4089 26.98 26.75 147.5 1,311.4 1,807.4 1,411.4 1.28 2.28 0.15 S-LINE-5113 21 372 Unknown 0.0020 S-MH-3574 S-MH-3575 6.26 5.44 391.2 3,648.0 4,807.0 3,347.9 1.44 4.45 0.88 S-LINE-5116 24 60 Unknown 0.0010 S-MH-3591 S-MH-3870 3.43 3.36 391.2 3,648.0 4,807.0 3,477.4 1.38 3.41 0.60 p.1 M:\MARYSVILLE\11447_Sewer_Comp_Plan\Appendices\Appx G pipe_deficiencies_2017.xls Marysville Sewer Comprehensive Plan 2017 Modeled Pipe Deficiencies City Pipe Number Diameter (inches) Length (Ft)Material Slope (ft/ft) Upstream Manhole Downstream Manhole Upstream Invert (ft) Downstream Invert (ft) Peakable (Residential) Flow (gpm) Unpeakable (Commercial / I&I) Flow (gpm) Total Flow (gpm) Design Capacity (gpm) Modeled Flow to Design Flow Ratio Velocity (ft/s) Upstream Surcharge Depth (ft) S-LINE-5117 24 395 Unknown 0.0010 S-MH-3870 S-MH-3594 3.36 3.01 391.2 3,648.0 4,807.0 3,030.5 1.59 3.41 0.54 S-LINE-5119 21 71 Unknown 0.0040 S-MH-3585 S-MH-3574 6.61 6.36 391.2 3,648.0 4,807.0 4,231.3 1.14 4.45 0.86 S-LINE-5218 15 417 Unknown 0.0000 S-MH-3581 S-MH-3582 8.81 8.78 54.0 1,871.5 2,067.7 246.6 8.39 3.75 2.22 S-LINE-5974 18 333 PVC 0.0010 S-MH-4289 S-MH-4290 49.16 48.84 29.9 67.2 177.0 146.5 1.21 0.22 0.15 S-LINE-624 18 330 Unknown 0.0020 S-MH-4862 S-MH-327 12.22 11.53 274.7 1,617.0 2,468.9 2,161.6 1.14 3.11 0.22 S-LINE-6493 30 24 PVC 0.0000 S-MH-4552 S-MH-4551 93.28 93.28 97.7 763.9 1,104.9 583.7 1.89 0.50 0.00 S-LINE-6534 12 185 PVC 0.0030 S-MH-4586 S-MH-4584 108.26 107.76 97.5 508.9 849.3 833.5 1.02 2.41 0.02 S-LINE-661 21 307 Concrete 0.0000 MH-13 S-MH-432 13.44 13.30 0.5 1,711.4 1,713.2 1,522.7 1.13 1.59 2.09 S-LINE-664 21 315 Unknown 0.0000 S-MH-328 S-MH-469 11.83 11.81 0.5 1,711.4 1,713.2 568.2 3.02 1.59 3.42 S-LINE-675 24 368 Concrete 0.0010 S-MH-651 S-MH-624 21.77 21.57 745.4 1,774.9 3,814.3 2,373.4 1.61 2.71 0.32 S-LINE-703 21 259 Concrete 0.0000 S-MH-591 S-MH-597 40.83 40.80 379.9 467.1 1,596.2 767.4 2.08 1.48 0.10 S-LINE-711 18 252 Concrete 0.0010 S-MH-670 S-MH-671 43.09 42.84 379.9 467.1 1,596.2 1,488.9 1.07 2.01 0.04 S-LINE-712 18 121 Concrete 0.0000 S-MH-669 S-MH-670 43.16 43.16 379.9 467.1 1,596.2 149.5 10.68 2.01 0.14 S-LINE-713 18 308 Concrete 0.0010 S-MH-679 S-MH-669 43.47 43.16 356.4 435.4 1,502.3 1,499.7 1.00 1.89 0.14 S-LINE-714 18 343 Concrete 0.0010 S-MH-682 S-MH-679 43.86 43.52 356.4 435.4 1,502.3 1,488.3 1.01 1.89 0.10 S-LINE-716 18 182 Concrete 0.0010 S-MH-692 S-MH-690 44.44 44.26 356.4 435.4 1,502.3 1,486.6 1.01 1.89 0.01 S-LINE-717 18 423 Concrete 0.0010 S-MH-700 S-MH-697 45.62 45.28 356.4 435.4 1,502.3 1,340.2 1.12 1.89 0.09 S-LINE-731 12 289 PVC 0.0020 S-MH-717 S-MH-702 47.24 46.76 191.1 240.8 860.0 653.4 1.32 2.44 0.36 S-LINE-7446 12 114 PVC 0.0010 S-MH-3505 S-MH-4595 110.51 110.40 91.2 342.5 662.9 498.0 1.33 1.88 1.22 S-LINE-852 12 219 PVC 0.0020 S-MH-733 S-MH-717 47.61 47.24 179.8 228.2 815.5 659.0 1.24 2.31 0.56 p.2 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!(Surcharged Manhole (<0.5') !(Surcharged Manhole (>0.5') "Modeled Pump Station Modeled Force Main Sanitary Sewer Pipe Deficient Sewer Pipe Subbasin Parcel ³ 0 3,400 6,8001,700 Feet Note: Pipeline identification labels are shown on Exhibit IV and surcharge results may be found in Appendix G. Marysville Sewer Comprehensive Plan 2031 Modeled Pipe Deficiencies City Pipe Number Diameter (inches)Length (Ft)Material Slope (ft/ft) Upstream Manhole Downstream Manhole Upstream Invert (ft) Downstream Invert (ft) Peakable (Residential) Flow (gpm) Unpeakable (Commercial / I&I) Flow (gpm) Total Flow (gpm) Design Capacity (gpm) Modeled Flow to Design Flow Ratio Velocity (ft/s) Upstream Surcharge Depth (ft) S-LINE-2488 15 161 PVC 0.0000 S-MH-1834 S-MH-1838 47.90 47.89 168.1 93.7 647.9 229.1 2.83 1.18 0.07 S-LINE-2414 10 85 PVC 0.0000 MH-170 S-MH-1845 46.60 46.58 14.3 100.7 153.3 151.2 1.01 0.63 0.001 S-LINE-1909 18 274 Unknown 0.0010 S-MH-1558 MH-110 40.15 39.90 248.3 1,072.1 1,850.8 1,427.9 1.30 2.33 0.227 S-LINE-1910 18 340 Unknown 0.0010 MH-110 S-MH-1568 39.90 39.43 248.3 1,072.1 1,850.8 1,757.6 1.05 2.33 0.054 S-LINE-1912 18 396 Unknown 0.0020 S-MH-1567 S-MH-1566 38.79 38.17 263.7 1,204.8 2,026.2 1,870.5 1.08 2.56 0.112 S-LINE-664 21 315 Unknown 0.0000 S-MH-328 S-MH-469 11.83 11.81 1.3 1,406.4 1,411.2 568.2 2.48 1.31 2.234 S-LINE-5218 15 417 Unknown 0.0000 S-MH-3581 S-MH-3582 8.81 8.78 89.5 1,589.1 1,904.1 246.6 7.72 3.46 1.8 S-LINE-510 18 258 Unknown 0.0010 S-MH-379 S-MH-4089 26.98 26.75 294.6 1,353.7 2,258.3 1,411.4 1.60 2.85 0.363 S-LINE-554 18 295 Unknown 0.0020 S-MH-458 S-MH-380 25.83 25.22 295.4 1,432.1 2,338.8 2,149.6 1.09 2.95 0.117 S-LINE-545 18 373 Unknown 0.0020 S-MH-353 S-MH-562 23.95 23.15 330.1 1,460.6 2,458.3 2,189.2 1.12 3.10 0.557 S-LINE-547 18 383 Unknown 0.0020 S-MH-562 S-MH-563 23.15 22.45 330.1 1,460.6 2,458.3 2,020.9 1.22 3.10 0.342 S-LINE-616 18 197 CI 0.0020 S-MH-440 S-MH-441 19.75 19.37 330.1 1,460.6 2,458.3 2,249.2 1.09 3.10 0.077 S-LINE-620 18 329 PVC 0.0030 S-MH-350 S-MH-346 16.91 16.07 349.9 1,558.9 2,608.6 2,388.6 1.09 3.29 0.168 S-LINE-624 18 330 Unknown 0.0020 S-MH-4862 S-MH-327 12.22 11.53 427.7 1,694.1 2,949.8 2,161.6 1.37 3.72 0.603 S-LINE-635 21 307 PVC 0.0010 S-MH-326 S-MH-324 10.54 10.13 427.7 1,694.1 2,949.8 2,605.9 1.13 2.73 0.192 S-LINE-5109 21 240 PVC 0.0010 S-MH-324 S-MH-3551 10.13 9.79 427.7 1,694.1 2,949.8 2,683.9 1.10 2.73 0.074 S-LINE-5119 21 71 Unknown 0.0040 S-MH-3585 S-MH-3574 6.61 6.36 582.9 3,465.5 5,112.5 4,231.3 1.21 4.74 1.123 S-LINE-5113 21 372 Unknown 0.0020 S-MH-3574 S-MH-3575 6.26 5.44 582.9 3,465.5 5,112.5 3,347.9 1.53 4.74 1.105 S-LINE-5116 24 60 Unknown 0.0010 S-MH-3591 S-MH-3870 3.43 3.36 582.9 3,465.5 5,112.5 3,477.4 1.47 3.63 0.744 S-LINE-5117 24 395 Unknown 0.0010 S-MH-3870 S-MH-3594 3.36 3.01 582.9 3,465.5 5,112.5 3,030.5 1.69 3.63 0.662 S-LINE-5227 24 141 Unknown 0.0020 S-MH-3594 S-MH-3868 3.01 2.66 582.9 3,465.5 5,112.5 5,072.3 1.01 3.63 0.008 S-LINE-2099 12 36 PVC 0.0010 S-MH-900 S-MH-857 51.80 51.78 92.2 163.4 487.0 377.9 1.29 1.38 0.186 S-LINE-2097 12 338 PVC 0.0010 S-MH-1606 S-MH-1605 51.61 51.23 131.6 204.0 652.5 537.6 1.21 1.85 0.183 S-LINE-1010 15 360 Concrete 0.0000 S-MH-708 S-MH-706 48.61 48.61 131.6 204.0 652.5 91.9 7.10 1.19 0.182 S-LINE-1011 15 101 Concrete 0.0000 S-MH-704 S-MH-703 47.09 47.09 158.6 246.4 773.8 91.9 8.42 1.41 0.072 S-LINE-852 12 219 PVC 0.0020 S-MH-733 S-MH-717 47.61 47.24 207.1 286.8 951.3 659.0 1.44 2.70 1.18 S-LINE-731 12 289 PVC 0.0020 S-MH-717 S-MH-702 47.24 46.76 217.9 301.7 996.1 653.4 1.52 2.83 0.775 S-LINE-717 18 423 Concrete 0.0010 S-MH-700 S-MH-697 45.62 45.28 376.5 548.1 1,668.2 1,340.2 1.25 2.10 0.19 S-LINE-1707 18 226 Concrete 0.0010 S-MH-697 S-MH-692 44.72 44.49 376.5 548.1 1,668.2 1,508.0 1.11 2.10 0.345 S-LINE-716 18 182 Concrete 0.0010 S-MH-692 S-MH-690 44.44 44.26 376.5 548.1 1,668.2 1,486.6 1.12 2.10 0.342 S-LINE-715 18 297 Concrete 0.0010 S-MH-690 S-MH-682 44.21 43.91 376.5 548.1 1,668.2 1,502.4 1.11 2.10 0.344 S-LINE-714 18 343 Concrete 0.0010 S-MH-682 S-MH-679 43.86 43.52 376.5 548.1 1,668.2 1,488.3 1.12 2.10 0.322 S-LINE-713 18 308 Concrete 0.0010 S-MH-679 S-MH-669 43.47 43.16 376.5 548.1 1,668.2 1,499.7 1.11 2.10 0.282 S-LINE-712 18 121 Concrete 0.0000 S-MH-669 S-MH-670 43.16 43.16 399.8 587.2 1,769.0 149.5 11.83 2.23 0.206 S-LINE-711 18 252 Concrete 0.0010 S-MH-670 S-MH-671 43.09 42.84 399.8 587.2 1,769.0 1,488.9 1.19 2.23 0.105 S-LINE-1462 24 367 Unknown 0.0000 S-MH-3608 S-MH-3802 24.67 24.57 347.1 2,093.3 3,135.6 1,680.5 1.87 2.22 0.523 S-LINE-990 24 491 Concrete 0.0010 S-MH-3802 S-MH-3801 24.57 24.27 347.1 2,093.3 3,135.6 2,516.5 1.25 2.22 0.272 S-LINE-989 24 400 Concrete 0.0000 S-MH-642 S-MH-641 22.47 22.27 358.6 2,111.9 3,184.6 2,276.5 1.40 2.26 0.875 S-LINE-703 21 259 Concrete 0.0000 S-MH-591 S-MH-597 40.83 40.80 399.8 587.2 1,769.0 767.4 2.31 1.64 0.13 S-LINE-675 24 368 Concrete 0.0010 S-MH-651 S-MH-624 21.77 21.57 833.4 2,847.0 5,097.9 2,373.4 2.15 3.62 0.729 S-LINE-2549 12 141 Unknown 0.0020 S-MH-1993 S-MH-1992 65.23 64.94 190.0 283.0 899.1 727.1 1.24 2.55 2.343 S-LINE-2547 12 181 Unknown 0.0030 S-MH-1992 S-MH-1995 64.94 64.42 190.0 283.0 899.1 859.4 1.05 2.55 2.187 S-LINE-2546 12 183 Unknown 0.0020 S-MH-1995 S-MH-1994 64.42 63.97 190.0 283.0 899.1 795.1 1.13 2.55 2.135 S-LINE-2545 12 355 Unknown 0.0020 S-MH-1994 S-MH-1998 63.97 63.13 190.0 283.0 899.1 779.9 1.15 2.55 2.007 S-LINE-2544 12 133 Unknown 0.0000 S-MH-1998 S-MH-1999 63.13 63.08 190.0 283.0 899.1 310.9 2.89 2.55 1.725 S-LINE-2543 12 179 Unknown 0.0030 S-MH-1999 S-MH-1997 63.08 62.60 190.0 283.0 899.1 830.3 1.08 2.55 1.354 S-LINE-2540 12 208 Unknown 0.0030 S-MH-1997 S-MH-2034 62.60 62.01 190.0 283.0 899.1 853.9 1.05 2.55 1.269 S-LINE-2214 12 98 PVC 0.0010 S-MH-2034 S-MH-1661 62.01 61.94 190.0 283.0 899.1 428.5 2.10 2.55 1.201 S-LINE-2213 12 283 PVC 0.0020 S-MH-1661 S-MH-1658 61.94 61.32 190.0 283.0 899.1 750.5 1.20 2.55 0.962 S-LINE-2203 12 407 DI 0.0030 S-MH-1657 S-MH-1651 57.50 56.45 200.3 531.5 1,176.7 814.4 1.45 3.34 3.094 S-LINE-2199 12 242 DI 0.0030 S-MH-1651 S-MH-1753 56.45 55.80 200.3 531.5 1,176.7 830.9 1.42 3.34 1.941 S-LINE-2198 12 203 DI 0.0020 S-MH-1753 S-MH-1754 55.80 55.30 216.6 531.5 1,222.3 795.7 1.54 3.47 1.281 S-LINE-2197 12 109 PVC 0.0010 S-MH-1754 S-MH-1755 55.30 55.14 216.6 531.5 1,222.3 614.3 1.99 3.47 0.595 S-LINE-2195 12 58 PVC 0.0040 S-MH-1755 S-MH-4607 55.14 54.92 216.6 531.5 1,222.3 987.5 1.24 3.47 0.119 S-LINE-2185 18 389 Concrete 0.0010 S-MH-1746 S-MH-1748 51.06 50.75 353.6 725.7 1,785.2 1,334.5 1.34 2.25 0.355 S-LINE-2184 18 388 Concrete 0.0010 S-MH-1748 S-MH-1729 50.75 50.30 353.6 725.7 1,785.2 1,609.9 1.11 2.25 0.107 S-LINE-2371 8 219 PVC 0.0000 S-MH-3769 S-MH-1422 45.74 45.67 28.6 21.3 126.5 97.2 1.30 0.81 0.049 S-LINE-475 48 74 Clay 0.0000 S-MH-540 S-MH-541 20.94 20.94 1,098.5 6,323.4 9,133.2 2,044.3 4.47 1.62 0.015 S-LINE-5234 30 29 DI 0.0010 S-MH-533 S-MH-532 11.92 11.90 845.5 2,881.1 5,158.5 4,847.6 1.06 2.34 0.037 S-LINE-431 30 277 DI 0.0010 S-MH-532 S-MH-529 11.90 11.69 845.5 2,881.1 5,158.5 5,082.5 1.02 2.34 0.034 S-LINE-484 30 237 Unknown 0.0010 S-MH-527 S-MH-549 11.30 11.12 845.5 2,881.1 5,158.5 5,087.1 1.01 2.34 0.025 P.1 M:\MARYSVILLE\11447_Sewer_Comp_Plan\Appendices\Appx G pipe_deficiencies_2031.xls Marysville Sewer Comprehensive Plan 2031 Modeled Pipe Deficiencies City Pipe Number Diameter (inches)Length (Ft)Material Slope (ft/ft) Upstream Manhole Downstream Manhole Upstream Invert (ft) Downstream Invert (ft) Peakable (Residential) Flow (gpm) Unpeakable (Commercial / I&I) Flow (gpm) Total Flow (gpm) Design Capacity (gpm) Modeled Flow to Design Flow Ratio Velocity (ft/s) Upstream Surcharge Depth (ft) S-LINE-5156 30 235 PVC 0.0010 S-MH-3563 MH-1361 10.75 10.57 845.5 2,881.1 5,158.5 5,108.7 1.01 2.34 0.018 S-LINE-5159 30 271 PVC 0.0010 MH-1361 MH-1362 10.57 10.37 845.5 2,881.1 5,158.5 5,014.6 1.03 2.34 0.013 S-LINE-4555 10 298 PVC 0.0010 S-MH-3242 S-MH-3241 112.73 112.55 51.0 272.3 457.8 242.3 1.89 1.87 5.784 S-LINE-4479 10 274 PVC 0.0010 S-MH-3203 S-MH-3204 112.20 111.96 72.7 76.6 338.3 291.8 1.16 1.38 5.805 S-LINE-5013 12 113 PVC 0.0010 S-MH-3204 S-MH-3522 111.96 111.86 123.7 348.9 772.4 477.0 1.62 2.19 5.554 S-LINE-5012 12 188 PVC 0.0010 S-MH-3522 S-MH-3513 111.86 111.64 123.7 348.9 772.4 548.5 1.41 2.19 5.39 S-LINE-5010 12 307 PVC 0.0010 S-MH-3513 S-MH-3521 111.52 111.18 123.7 348.9 772.4 533.6 1.45 2.19 5.292 S-LINE-5009 12 317 PVC 0.0010 S-MH-3521 S-MH-3510 111.16 110.85 123.7 348.9 772.4 501.4 1.54 2.19 4.936 S-LINE-5008 12 307 PVC 0.0010 S-MH-3510 S-MH-3505 110.81 110.55 158.6 378.0 905.4 466.6 1.94 2.57 4.547 S-LINE-7446 12 114 PVC 0.0010 S-MH-3505 S-MH-4595 110.51 110.40 158.6 378.0 905.4 498.0 1.82 2.57 3.863 S-LINE-5005 12 283 PVC 0.0000 S-MH-3506 S-MH-4594 110.15 110.05 169.1 553.1 1,110.2 301.4 3.68 3.15 3.217 S-LINE-5004 12 208 PVC 0.0010 S-MH-4594 S-MH-4596 110.05 109.81 169.1 553.1 1,110.2 544.6 2.04 3.15 1.953 S-LINE-4849 14 331 Asbestos Cement 0.0000 S-MH-3424 S-MH-3425 112.45 112.36 33.0 337.0 457.9 398.8 1.15 0.95 0.029 S-LINE-4246 30 178 Concrete 0.0000 S-MH-3025 S-MH-3024 83.10 83.08 217.3 2,198.9 2,891.7 1,956.7 1.48 1.31 0.024 S-LINE-3881 12 233 Concrete 0.0000 MH-212 S-MH-2713 85.83 85.82 0.4 121.3 122.8 105.0 1.17 0.35 3.893 S-LINE-3833 18 481 Concrete 0.0020 S-MH-2589 S-MH-2757 80.90 80.08 209.5 2,094.7 2,765.9 1,951.8 1.42 3.49 6.637 S-LINE-3586 18 497 Concrete 0.0020 S-MH-2757 MH-102 80.08 79.03 209.5 2,094.7 2,765.9 2,172.8 1.27 3.49 5.8 S-LINE-3587 18 410 Concrete 0.0030 MH-102 S-MH-2702 79.03 77.75 209.5 2,225.7 2,896.9 2,641.3 1.10 3.65 5.138 S-LINE-3588 18 479 Concrete 0.0010 S-MH-2701 S-MH-2761 76.69 76.00 209.6 2,282.9 2,954.3 1,794.2 1.65 3.73 5.775 S-LINE-3589 18 467 Concrete 0.0020 S-MH-2761 S-MH-2684 76.00 74.89 209.6 2,282.9 2,954.3 2,304.7 1.28 3.73 4.583 S-LINE-3596 18 378 Concrete 0.0030 S-MH-2684 S-MH-2760 74.89 73.67 209.6 2,365.8 3,037.2 2,685.6 1.13 3.83 3.857 S-LINE-3597 18 369 Concrete 0.0030 S-MH-2760 S-MH-2759 73.67 72.64 215.2 2,413.0 3,100.0 2,497.5 1.24 3.91 3.507 S-LINE-1171 18 362 Concrete 0.0030 S-MH-2759 MH-1422 72.64 71.43 215.2 2,413.0 3,100.0 2,733.0 1.13 3.91 2.94 S-LINE-3604 18 360 Concrete 0.0030 MH-1422 MH-166 71.43 70.33 215.2 2,413.0 3,100.0 2,613.1 1.19 3.91 2.583 S-LINE-3300 21 264 Concrete 0.0010 S-MH-3861 S-MH-3860 69.84 69.51 224.1 2,486.8 3,198.4 2,521.1 1.27 2.96 2.195 S-LINE-3196 21 390 Concrete 0.0020 S-MH-3860 MH-221 69.51 68.72 229.4 2,494.1 3,220.4 3,209.3 1.00 2.98 1.99 S-LINE-3200 21 407 Concrete 0.0010 MH-221 S-MH-2383 68.72 68.20 229.4 2,494.1 3,220.4 2,548.8 1.26 2.98 1.979 S-LINE-3201 21 14 Concrete 0.0010 S-MH-2383 S-MH-2382 68.20 68.18 257.5 2,615.8 3,420.0 2,695.1 1.27 3.17 1.663 S-LINE-3296 21 454 Concrete 0.0020 S-MH-2708 S-MH-3792 67.91 66.89 294.7 2,659.4 3,564.2 3,379.9 1.06 3.30 1.757 S-LINE-3295 21 466 Concrete 0.0020 S-MH-3792 S-MH-3793 66.89 66.07 294.7 2,659.4 3,564.2 2,991.2 1.19 3.30 1.634 S-LINE-3294 21 472 Concrete 0.0020 S-MH-3793 S-MH-3794 66.07 65.17 294.7 2,659.4 3,564.2 3,113.7 1.15 3.30 1.282 S-LINE-3293 21 478 Concrete 0.0020 S-MH-3794 S-MH-2364 65.17 64.12 294.7 2,659.4 3,564.2 3,342.0 1.07 3.30 0.995 S-LINE-3194 21 173 Concrete 0.0020 S-MH-2364 S-MH-2363 64.12 63.72 304.3 2,681.2 3,611.2 3,428.8 1.05 3.35 0.842 S-LINE-3191 21 347 Concrete 0.0020 S-MH-2363 S-MH-2362 63.72 63.13 318.9 2,683.8 3,652.1 2,940.3 1.24 3.38 0.796 S-LINE-3188 21 420 Concrete 0.0020 S-MH-2362 S-MH-2384 63.13 62.48 324.3 2,685.8 3,668.3 2,805.2 1.31 3.40 0.469 S-LINE-3185 21 45 Concrete 0.0020 S-MH-2403 S-MH-2405 44.97 44.87 324.3 2,685.8 3,668.3 3,361.4 1.09 3.40 0.02 S-LINE-5007 12 200 PVC 0.0010 S-MH-4595 S-MH-3506 110.40 110.20 158.6 378.0 905.4 507.0 1.79 2.57 3.608 S-LINE-5738 8 112 PVC 0.0040 S-MH-4096 S-MH-55 260.20 259.71 91.3 61.0 381.7 359.7 1.06 2.44 0.064 S-LINE-5737 8 245 PVC 0.0040 S-MH-219 S-MH-4096 261.30 260.20 91.3 61.0 381.7 364.4 1.05 2.44 0.175 S-LINE-164 8 111 PVC 0.0040 S-MH-215 S-MH-216 267.58 267.13 91.3 61.0 381.7 346.2 1.10 2.44 0.099 S-LINE-163 8 242 0.0040 S-MH-214 S-MH-215 268.66 267.61 91.3 61.0 381.7 358.2 1.07 2.44 0.216 S-LINE-160 8 158 PVC 0.0050 S-MH-63 S-MH-212 271.22 270.47 91.3 61.0 381.7 374.7 1.02 2.44 0.031 S-LINE-6493 30 24 PVC 0.0000 S-MH-4552 S-MH-4551 93.28 93.28 186.3 817.3 1,423.0 583.7 2.44 0.65 0.001 S-LINE-6504 15 301 PVC 0.0010 S-MH-4562 S-MH-4561 101.85 101.43 177.7 685.2 1,266.6 1,085.9 1.17 2.30 0.155 S-LINE-6505 15 301 PVC 0.0020 S-MH-4563 S-MH-4562 102.40 101.90 177.7 685.2 1,266.6 1,184.8 1.07 2.30 0.179 S-LINE-6535 12 396 PVC 0.0030 S-MH-4584 S-MH-4583 107.66 106.52 169.1 553.1 1,110.2 860.3 1.29 3.15 0.768 S-LINE-6534 12 185 PVC 0.0030 S-MH-4586 S-MH-4584 108.26 107.76 169.1 553.1 1,110.2 833.5 1.33 3.15 1.059 S-LINE-6533 12 262 PVC 0.0040 S-MH-4587 S-MH-4586 109.28 108.36 169.1 553.1 1,110.2 950.1 1.17 3.15 1.302 S-LINE-7441 12 87 PVC 0.0040 S-MH-4596 S-MH-4587 109.71 109.33 169.1 553.1 1,110.2 1,059.6 1.05 3.15 1.291 S-LINE-618 18 213 PVC 0.0020 S-MH-351 S-MH-350 17.49 17.01 349.9 1,558.9 2,608.6 2,244.1 1.16 3.29 0.241 S-LINE-5974 18 333 PVC 0.0010 S-MH-4289 S-MH-4290 49.16 48.84 105.9 71.9 438.9 146.5 3.00 0.55 2.569 S-LINE-11994 15 333 PVC 0.0040 S-MH-6727 S-MH-3546 12.09 10.80 89.5 1,589.1 1,904.1 1,809.4 1.05 3.46 2.283 S-LINE-11995 15 157 PVC 0.0040 S-MH-3546 S-MH-3547 10.70 10.12 89.5 1,589.1 1,904.1 1,766.9 1.08 3.46 2.236 S-LINE-11996 15 353 PVC 0.0020 S-MH-3547 S-MH-3548 10.02 9.48 89.5 1,589.1 1,904.1 1,137.0 1.68 3.46 2.239 S-LINE-3242 8 190 DI 0.0010 S-MH-2406 S-MH-2344 57.19 56.96 62.2 3.8 229.4 189.2 1.21 1.46 0.109 P.2 M:\MARYSVILLE\11447_Sewer_Comp_Plan\Appendices\Appx G pipe_deficiencies_2031.xls " " " " " " " !( !( !( !( !(!(!(!( !(!(!( !( !( !( !(!( !( !( !(!(!(!(!( !( !( !( !(!(!(!(!(!(!(!( !( !( !( !( !( !( !( !( !( !( !( !( !(!( !( !( !( !( !( !( !(!(!(!( !( !(!(!(!( !(!( !(!( !( !(!(!( !( !( !( !( !(!(!(!( !(!( !( !( !( !( !( !(!( !(!( !(!(!(!( !( !( !( !( !(!( !( !( !( !( !( !( !(!( !( !( !(!( !( !( !( !( !(!( !( !(!( !( !( !(!(!(!(!(!(!(!(!(!( !(!(!( !( !( !( !( !( !(!(!( !( !(!(!( !(!(!(!(!(!(!( !( !( !( !( !( !(!(!( !( !( !(!(!(!(!(!(!(!(!(!( !( !( !( !( !( !(!(!(!(!(!(!(!(!( !( !(!(!(!( !( !(!( !( !(!(!(!(!(!( !(!(!( !(!(!(!( !(!(!(!(!(!(!( !( !( !( !( !(!(!(!( !( !( !( !( !( !( !(!(!(!(!(!(!( !(!(!(!( !(!( !(!( !(!( !( !( !( !( !(!(!(!( !(!( !(!( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !( !( !( !( !(!(!(!(!(!(!(!(!(!(!(!(!(!( !(!(!(!(!(!(!(!( !( !( !( !(!(!(!(!(!( !(!(!( !( !(!(!(!(!(!( !( !(!(!(!(!(!(!(!(!( !(!( !( !( !(!( !(!(!( !(!(!(!(!(!(!(!( !(!(!(!(!(!(!(!(!( !( !( !( !( !( !( !(!(!( !( !(!( !( !(!( !( !( !( !( !(!(!( !(!(!(!(!(!( !(!( !( !(!(!( !( !(!(!( !( !(!( !( !( !( !(!(!( !(!( !(!(!(!(!(!( !( !( !(!(!(!(!(!(!( !( !(!( !( !(!( !(!(!(!(!(!(!(!( !( !( !(!(!(!(!(!(!(!(!(!(!(!(!(!( !(!(!( !(!(!( !( !(!(!( !(!( !(!( !(!( !(!(!(!(!( !( !( !( !(!( !(!(!(!(!(!( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !(!( !( !(!(!(!(!(!( !( !( !( !(!(!( !( !(!(!(!(!( !( !(!(!(!(!(!(!(!(!( !( !( !( !( !(!(!(!(!(!( !( !( !( !(!( !( !( !( !(!(!( !( !( !(!(!(!( !( !( !(!( !(!( !( !(!( !(!( !( !(!(!( !(!( !(!( !( !(!( !( !( !(!(!(!(!(!(!(!( !( !( !( !(!( !( !(!(!( !( !( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !( !(!( !( !( !( !( !(!( !(!(!(!(!(!(!(!(!(!( !( !( !( !( !( !( !(!( !(!(!(!(!( !(!(!(!( !(!( !( !(!(!( !( !(!(!(!(!( !( !(!( !(!( !(!(!( !(!(!( !( !( !( !(!( !( !( !( !( !( !(!(!(!(!(!(!( !(!(!(!( !(!(!(!(!(!( !( !(!(!(!(!(!( !( !( !(!(!(!(!(!(!( !(!(!( !( !( !(!(!(!(!(!(!(!(!(!( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !( !(!( !(!( !(!( !(!( !( !( !(!(!( !(!(!(!(!( !( !( !( !(!(!( !( !( !( !( !( !( !(!( !(!(!(!(!(!(!(!(!(!( !( !(!( !( !(!( !( !(!( !( !( !(!( !( !( !(!(!( !( !( !( !( !( !(!(!(!(!(!(!(!(!( !(!(!( !( !( !( !( !(!(!(!(!(!(!(!( !( !( !(!( !(!( !(!( !( !( !( !( !(!(!(!(!(!(!(!(!( !( !(!(!( !(!( !(!(!(!(!(!(!(!(!(!(!(!(!(!(!( !( !( !( !( !(!( !(!(!(!(!(!( !(!(!(!(!(!( !(!(!(!( !( !(!( !(!( !( !(!( !(!(!( !( !( !( !( !( !( !( !( !( !( !(!(!(!(!(!(!( !( !( !( !( !( !( !( !(!(!(!(!( !( !(!( !( !( !(!( !(!( !( !( !( !( !( !( !( !(!(!(!(!( !( !( !( !( !( !(!(!(!( !( !(!(!(!(!(!(!(!( !(!(!(!( !(!( !( !( !(!(!(!( !( !(!(!( !( !( !( !( !( !( !( !(!( !(!( !( !( !( !( !( !(!(!(!(!(!(!(!(!( !(!(!(!(!(!(!( !( !(!( !(!(!( !( !(!( !(!(!(!(!( !(!(!( !( 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A14 CE9 D6-3 A18-3 CE5-4 CW9 D7-2 CW5 F1 D6-1 CE1 F6 D7-1 CE5-6 CW6 A12-4 CE8 CE4 A12-1 A18-2 CE5-5 CITY OF MARYSVILLE SEWER COMPREHENSIVE PLAN FIGURE 7-7 MODEL RESULTS (Buildout w/ Improvements) M:\MARYSVILLE\11447_Sewer_Comp_Plan\Figures\Fig 7-7 Model Results Buildout.mxd Legend !(Modeled Manhole !(Surcharged Manhole (<0.5') !(Surcharged Manhole (>0.5') "Modeled Pump Station Modeled Force Main Sanitary Sewer Pipe Deficient Sewer Pipe Subbasin Parcel ³ 0 3,400 6,8001,700 Feet Note: Pipeline identification labels are shown on Exhibit IV and surcharge results may be found in Appendix G. Marysville Sewer Comprehensive Plan Buildout Modeled Pipe Deficiencies City Pipe Number Diameter (inches) Length (Ft)Material Slope (ft/ft) Upstream Manhole Downstream Manhole Upstream Invert (ft) Downstream Invert (ft) Peakable (Residential) Flow (gpm) Unpeakable (Commercial / I&I) Flow (gpm) Total Flow (gpm) Design Capacity (gpm) Modeled Flow to Design Flow Ratio Velocity (ft/s) Upstream Surcharge Depth (ft) S-LINE-1010 15 360 Concrete 0.0000 S-MH-708 S-MH-706 48.61 48.61 131.6 204.0 652.5 91.9 7.10 1.19 0.18 S-LINE-1011 15 101 Concrete 0.0000 S-MH-704 S-MH-703 47.09 47.09 158.6 246.4 773.8 91.9 8.42 1.41 0.07 S-LINE-11996 15 353 PVC 0.0020 S-MH-3547 S-MH-3548 10.02 9.48 89.5 1,589.1 1,904.1 1,343.7 1.42 3.46 1.79 S-LINE-1462 30 367 Unknown 0.0000 S-MH-3608 S-MH-3802 24.67 24.57 347.1 2,093.3 3,135.6 3,047.0 1.03 1.42 0.01 S-LINE-160 8 158 PVC 0.0050 S-MH-63 S-MH-212 271.22 270.47 91.3 61.0 381.7 374.7 1.02 2.44 0.03 S-LINE-163 8 242 0.0040 S-MH-214 S-MH-215 268.66 267.61 91.3 61.0 381.7 358.2 1.07 2.44 0.22 S-LINE-164 8 111 PVC 0.0040 S-MH-215 S-MH-216 267.58 267.13 91.3 61.0 381.7 346.2 1.10 2.44 0.10 S-LINE-1909 18 274 Unknown 0.0010 S-MH-1558 MH-110 40.15 39.90 248.3 1,072.1 1,850.8 1,427.9 1.30 2.33 0.23 S-LINE-1910 18 340 Unknown 0.0010 MH-110 S-MH-1568 39.90 39.43 248.3 1,072.1 1,850.8 1,757.6 1.05 2.33 0.05 S-LINE-1912 18 396 Unknown 0.0020 S-MH-1567 S-MH-1566 38.79 38.17 263.7 1,204.8 2,026.2 1,870.5 1.08 2.56 0.11 S-LINE-2028 18 237 Concrete 0.0020 S-MH-1523 S-MH-1522 45.52 45.07 421.5 944.1 2,183.3 2,059.9 1.06 2.75 0.06 S-LINE-2097 12 338 PVC 0.0010 S-MH-1606 S-MH-1605 51.61 51.23 131.6 204.0 652.5 537.6 1.21 1.85 0.18 S-LINE-2099 12 36 PVC 0.0010 S-MH-900 S-MH-857 51.80 51.78 92.2 163.4 487.0 377.9 1.29 1.38 0.19 S-LINE-2184 18 388 Concrete 0.0010 S-MH-1748 S-MH-1729 50.75 50.30 399.1 931.3 2,111.2 1,609.9 1.31 2.66 0.33 S-LINE-2185 18 389 Concrete 0.0010 S-MH-1746 S-MH-1748 51.06 50.75 399.1 931.3 2,111.2 1,334.5 1.58 2.66 0.80 S-LINE-2187 18 384 Concrete 0.0020 S-MH-1743 S-MH-1745 52.46 51.87 383.2 912.4 2,050.2 1,853.0 1.11 2.59 0.91 S-LINE-2197 15 109 PVC 0.0010 S-MH-1754 S-MH-1755 55.30 55.14 216.6 531.5 1,222.3 1,113.8 1.10 2.22 0.63 S-LINE-2213 12 283 PVC 0.0020 S-MH-1661 S-MH-1658 61.94 61.32 190.0 283.0 899.1 886.9 1.01 2.55 0.02 S-LINE-2214 12 98 PVC 0.0010 S-MH-2034 S-MH-1661 62.01 61.94 190.0 283.0 899.1 506.4 1.78 2.55 0.17 S-LINE-2371 8 219 PVC 0.0000 S-MH-3769 S-MH-1422 45.74 45.67 28.6 21.3 126.5 97.2 1.30 0.81 0.05 S-LINE-2414 10 85 PVC 0.0000 MH-170 S-MH-1845 46.60 46.58 14.3 100.7 153.3 151.2 1.01 0.63 0.00 S-LINE-2488 15 161 PVC 0.0000 S-MH-1834 S-MH-1838 47.90 47.89 168.1 93.7 647.9 229.1 2.83 1.18 0.07 S-LINE-2544 12 133 Unknown 0.0000 S-MH-1998 S-MH-1999 63.13 63.08 190.0 283.0 899.1 367.4 2.45 2.55 0.25 S-LINE-2549 12 141 Unknown 0.0020 S-MH-1993 S-MH-1992 65.23 64.94 190.0 283.0 899.1 859.3 1.05 2.55 0.03 S-LINE-3036 12 85 PVC 0.0020 MH-234 S-MH-2201 63.47 63.26 168.0 302.6 856.6 796.9 1.08 2.43 0.03 S-LINE-3037 12 453 PVC 0.0030 S-MH-2290 MH-234 64.71 63.47 168.0 302.6 856.6 838.8 1.02 2.43 0.09 S-LINE-3052 10 245 PVC 0.0030 S-MH-2306 S-MH-2305 66.73 65.97 96.7 244.2 582.0 549.2 1.06 2.38 0.10 S-LINE-3053 10 140 PVC 0.0030 S-MH-2307 S-MH-2306 67.15 66.73 96.7 244.2 582.0 540.0 1.08 2.38 0.17 S-LINE-3055 8 224 PVC 0.0040 MH-156 S-MH-2260 76.83 75.95 72.1 235.3 495.1 340.8 1.45 3.16 2.12 S-LINE-3056 8 272 PVC 0.0040 S-MH-2260 S-MH-2259 75.95 74.81 72.1 235.3 495.1 352.1 1.41 3.16 1.13 S-LINE-3084 10 314 PVC 0.0030 S-MH-2235 S-MH-2307 67.98 67.15 96.7 244.2 582.0 506.9 1.15 2.38 0.44 S-LINE-3242 8 190 DI 0.0010 S-MH-2406 S-MH-2344 57.19 56.96 62.2 3.8 229.4 189.2 1.21 1.46 0.11 S-LINE-3806 36 372 Concrete 0.0010 S-MH-2742 S-MH-2741 66.52 66.32 2,078.5 5,747.6 10,530.1 6,959.9 1.51 3.32 0.50 S-LINE-3850 36 302 Concrete 0.0010 S-MH-2739 S-MH-2738 65.67 65.32 2,100.3 5,776.7 10,598.1 10,218.6 1.04 3.34 0.03 S-LINE-3851 36 359 Concrete 0.0010 S-MH-2741 S-MH-2740 66.32 66.11 2,078.5 5,747.6 10,530.1 7,259.8 1.45 3.32 0.24 S-LINE-3959 24 454 Concrete 0.0010 S-MH-2817 S-MH-2818 87.86 87.53 380.2 1,963.4 3,093.3 2,744.8 1.13 2.19 0.09 S-LINE-4246 30 178 Concrete 0.0000 S-MH-3025 S-MH-3024 83.10 83.08 467.0 2,198.9 3,558.6 1,956.7 1.82 1.62 0.05 S-LINE-431 30 277 DI 0.0010 S-MH-532 S-MH-529 11.90 11.69 845.5 2,894.1 5,171.5 5,082.5 1.02 2.35 0.04 S-LINE-438 30 294 Unknown 0.0010 S-MH-528 S-MH-527 11.53 11.30 845.5 2,894.1 5,171.5 5,163.0 1.00 2.35 0.03 S-LINE-4479 10 274 PVC 0.0010 S-MH-3203 S-MH-3204 112.20 111.96 72.7 76.6 338.3 291.8 1.16 1.38 0.33 S-LINE-4555 10 298 PVC 0.0010 S-MH-3242 S-MH-3241 112.73 112.55 51.0 272.3 457.8 242.3 1.89 1.87 0.47 S-LINE-475 48 74 Clay 0.0000 S-MH-540 S-MH-541 20.94 20.94 1,289.2 7,185.7 10,338.9 2,044.3 5.06 1.83 0.02 S-LINE-484 30 237 Unknown 0.0010 S-MH-527 S-MH-549 11.30 11.12 845.5 2,894.1 5,171.5 5,087.1 1.02 2.35 0.03 S-LINE-4849 14 331 ASBESTOS CEMENT 0.0000 S-MH-3424 S-MH-3425 112.45 112.36 33.0 337.0 457.9 398.8 1.15 0.95 0.03 S-LINE-5004 15 208 PVC 0.0010 S-MH-4594 S-MH-4596 110.05 109.81 169.1 553.1 1,110.2 987.5 1.12 2.02 0.07 S-LINE-5005 15 283 PVC 0.0000 S-MH-3506 S-MH-4594 110.15 110.05 169.1 553.1 1,110.2 546.5 2.03 2.02 0.38 S-LINE-5008 15 307 PVC 0.0010 S-MH-3510 S-MH-3505 110.81 110.55 158.6 378.0 905.4 846.0 1.07 1.64 0.33 S-LINE-510 18 258 Unknown 0.0010 S-MH-379 S-MH-4089 26.98 26.75 294.6 1,353.7 2,258.3 1,411.4 1.60 2.85 0.36 S-LINE-5109 21 240 PVC 0.0010 S-MH-324 S-MH-3551 10.13 9.79 427.7 1,694.1 2,949.8 2,683.9 1.10 2.73 0.07 P.1 M:\MARYSVILLE\11447_Sewer_Comp_Plan\Appendices\Appx G pipe_deficiencies_buildout.xls Marysville Sewer Comprehensive Plan Buildout Modeled Pipe Deficiencies City Pipe Number Diameter (inches) Length (Ft)Material Slope (ft/ft) Upstream Manhole Downstream Manhole Upstream Invert (ft) Downstream Invert (ft) Peakable (Residential) Flow (gpm) Unpeakable (Commercial / I&I) Flow (gpm) Total Flow (gpm) Design Capacity (gpm) Modeled Flow to Design Flow Ratio Velocity (ft/s) Upstream Surcharge Depth (ft) S-LINE-5113 24 372 Unknown 0.0020 S-MH-3574 S-MH-3575 6.26 5.44 582.9 3,465.5 5,112.5 4,779.8 1.07 3.63 0.13 S-LINE-5154 30 230 PVC 0.0010 S-MH-3571 S-MH-3563 10.93 10.75 845.5 2,894.1 5,171.5 5,163.9 1.00 2.35 0.02 S-LINE-5156 30 235 PVC 0.0010 S-MH-3563 MH-1361 10.75 10.57 845.5 2,894.1 5,171.5 5,108.7 1.01 2.35 0.02 S-LINE-5159 30 271 PVC 0.0010 MH-1361 MH-1362 10.57 10.37 845.5 2,894.1 5,171.5 5,014.6 1.03 2.35 0.01 S-LINE-5218 15 417 Unknown 0.0000 S-MH-3581 S-MH-3582 8.81 8.78 89.5 1,589.1 1,904.1 246.6 7.72 3.46 1.80 S-LINE-5227 24 141 Unknown 0.0020 S-MH-3594 S-MH-3868 3.01 2.66 582.9 3,465.5 5,112.5 5,072.3 1.01 3.63 0.01 S-LINE-5234 30 29 DI 0.0010 S-MH-533 S-MH-532 11.92 11.90 845.5 2,894.1 5,171.5 4,847.6 1.07 2.35 0.05 S-LINE-545 18 373 Unknown 0.0020 S-MH-353 S-MH-562 23.95 23.15 330.1 1,460.6 2,458.3 2,189.2 1.12 3.10 0.56 S-LINE-547 18 383 Unknown 0.0020 S-MH-562 S-MH-563 23.15 22.45 330.1 1,460.6 2,458.3 2,020.9 1.22 3.10 0.34 S-LINE-554 18 295 Unknown 0.0020 S-MH-458 S-MH-380 25.83 25.22 295.4 1,432.1 2,338.8 2,149.6 1.09 2.95 0.12 S-LINE-5737 8 245 PVC 0.0040 S-MH-219 S-MH-4096 261.30 260.20 91.3 61.0 381.7 364.4 1.05 2.44 0.18 S-LINE-5738 8 112 PVC 0.0040 S-MH-4096 S-MH-55 260.20 259.71 91.3 61.0 381.7 359.7 1.06 2.44 0.06 S-LINE-5974 18 333 PVC 0.0010 S-MH-4289 S-MH-4290 49.16 48.84 105.9 71.9 438.9 146.5 3.00 0.55 2.57 S-LINE-616 18 197 CI 0.0020 S-MH-440 S-MH-441 19.75 19.37 330.1 1,460.6 2,458.3 2,249.2 1.09 3.10 0.08 S-LINE-618 18 213 PVC 0.0020 S-MH-351 S-MH-350 17.49 17.01 349.9 1,558.9 2,608.6 2,244.1 1.16 3.29 0.24 S-LINE-620 18 329 PVC 0.0030 S-MH-350 S-MH-346 16.91 16.07 349.9 1,558.9 2,608.6 2,388.6 1.09 3.29 0.17 S-LINE-635 21 307 PVC 0.0010 S-MH-326 S-MH-324 10.54 10.13 427.7 1,694.1 2,949.8 2,605.9 1.13 2.73 0.19 S-LINE-6493 30 24 PVC 0.0000 S-MH-4552 S-MH-4551 93.28 93.28 1,074.0 1,714.4 4,480.0 583.7 7.68 2.03 0.01 S-LINE-6494 30 95 PVC 0.0000 S-MH-4553 S-MH-4552 93.42 93.38 1,074.0 1,714.4 4,480.0 3,787.7 1.18 2.03 0.02 S-LINE-6504 15 301 PVC 0.0010 S-MH-4562 S-MH-4561 101.85 101.43 177.7 685.2 1,266.6 1,085.9 1.17 2.30 0.16 S-LINE-6505 15 301 PVC 0.0020 S-MH-4563 S-MH-4562 102.40 101.90 177.7 685.2 1,266.6 1,184.8 1.07 2.30 0.18 S-LINE-6603 18 59 PVC 0.0010 S-MH-4610 S-MH-4611 52.85 52.77 373.5 899.1 2,011.3 1,740.7 1.16 2.54 1.32 S-LINE-664 21 315 Unknown 0.0000 S-MH-328 S-MH-469 11.83 11.81 1.3 1,406.4 1,411.2 568.2 2.48 1.31 1.18 S-LINE-675 30 368 Concrete 0.0010 S-MH-651 S-MH-624 21.77 21.57 833.4 2,860.0 5,110.9 4,303.3 1.19 2.32 0.08 S-LINE-6778 12 324 PVC 0.0030 S-MH-4720 S-MH-4719 67.79 66.83 139.9 456.2 930.7 872.7 1.07 2.64 0.14 S-LINE-6779 12 337 PVC 0.0030 S-MH-4721 S-MH-4720 68.82 67.89 139.9 456.2 930.7 842.3 1.11 2.64 0.25 S-LINE-6780 12 268 PVC 0.0030 S-MH-4722 S-MH-4721 69.76 68.92 139.9 456.2 930.7 897.6 1.04 2.64 0.22 S-LINE-6783 12 121 PVC 0.0020 S-MH-4725 S-MH-4722 70.14 69.86 139.9 456.2 930.7 771.3 1.21 2.64 0.25 S-LINE-6784 12 149 PVC 0.0020 S-MH-4726 S-MH-4725 70.57 70.24 139.9 456.2 930.7 754.5 1.23 2.64 0.32 S-LINE-6785 12 129 PVC 0.0020 S-MH-4729 S-MH-4726 70.96 70.67 139.9 456.2 930.7 760.2 1.22 2.64 0.37 S-LINE-6788 12 278 PVC 0.0020 S-MH-4730 S-MH-4729 71.67 71.06 139.9 456.2 930.7 751.0 1.24 2.64 0.60 S-LINE-6793 12 136 PVC 0.0020 S-MH-4735 S-MH-4730 72.04 71.77 139.9 456.2 930.7 714.4 1.30 2.64 0.69 S-LINE-6794 12 135 PVC 0.0020 S-MH-4736 S-MH-4735 72.42 72.14 139.9 456.2 930.7 730.2 1.28 2.64 0.77 S-LINE-6797 12 221 PVC 0.0020 S-MH-4739 S-MH-4736 72.98 72.52 139.9 456.2 930.7 731.5 1.27 2.64 0.96 S-LINE-703 21 259 Concrete 0.0000 S-MH-591 S-MH-597 40.83 40.80 399.8 600.2 1,782.0 767.4 2.32 1.65 0.13 S-LINE-711 18 252 Concrete 0.0010 S-MH-670 S-MH-671 43.09 42.84 399.8 600.2 1,782.0 1,759.6 1.01 2.25 0.01 S-LINE-712 18 121 Concrete 0.0000 S-MH-669 S-MH-670 43.16 43.16 399.8 600.2 1,782.0 176.7 10.09 2.25 0.12 S-LINE-717 18 423 Concrete 0.0010 S-MH-700 S-MH-697 45.62 45.28 376.5 561.1 1,681.2 1,583.9 1.06 2.12 0.05 S-LINE-7446 15 114 PVC 0.0010 S-MH-3505 S-MH-4595 110.51 110.40 158.6 378.0 905.4 903.0 1.00 1.64 0.33 P.2 M:\MARYSVILLE\11447_Sewer_Comp_Plan\Appendices\Appx G pipe_deficiencies_buildout.xls APPENDIX F EFFLUENT TSS AND CBOD TRENDING CHARTS ! ! !" #!$%$%$%# $%&’$%($%#!$)$)$)# $)&’$)($)#!$*$*$*# $*&’$*($*#!$+$+$+# $+&’$+($+#!$$$# $&’$($ !" "! ! !!"#$#$#$"#$%#$&#$"#’#’#’"#’%#’&#’"#(#(#("#(%#(&#("#)#)#)"#)%#)&#)"#!#!#!"#!%#!&#! APPENDIX G CMOM CHECKLIST Page i About the CMOM Program Self Assessment Checklist Introduction A sanitary sewer collection system is a vital element of any community’s infrastructure and a critical component of the wastewater treatment process. The nation’s sanitary sewer infrastructure has been built over the last 100 years or more using a variety of materials, design standards, installation techniques, and maintenance practices. As this valuable infrastructure ages, the importance of preventive and predictive maintenance increases. What is CMOM? CMOM stands for “capacity, management, operations, and maintenance.” It is a flexible, dynamic framework for municipalities to identify and incorporate widely-accepted wastewater industry practices to: • Better manage, operate, and maintain collection systems • Investigate capacity constrained areas of the collection system • Respond to sanitary sewer overflow (SSO) events The CMOM approach helps municipal wastewater utility operators provide a high level of service to customers and reduce regulatory non-compliance. CMOM can help utilities optimize use of human and material resources by shifting maintenance activities from “reactive” to “predictive” - often leading to cost savings through avoided overtime, emergency construction costs, increased insurance premiums, and the possibility of lawsuits. CMOM information and documentation can also help improve communications with the public, other municipal works, and regional planning organizations, and regulators. In CMOM planning, the utility selects performance goal targets, and designs CMOM activities to meet the goals. The CMOM planning framework covers operation and maintenance (O&M) planning, capacity assessment and assurance, capital improvement planning, and financial management planning. Information collection and management practices are used to track how well each CMOM activity is meeting the performance goals, and whether overall system efficiency is improving. On an ongoing basis, activities are reviewed and adjusted to better meet the change. For instance, an initial goal may be to develop a geographic information system (GIS) of the system. Once the GIS is complete, a new goal might be to use the GIS to track emergency calls and use the information to improve maintenance planning. An important component of a successful CMOM program is to periodically collect information on current systems and activities and develop a “snapshot-in-time” analysis. From this analysis, the utility establishes its performance goals and plans its CMOM program activities. Additional information describing CMOM can be found at www.epa.gov/npdes/sso or www.epa.gov/region4/water/wpeb/pdfs/self-audit_review2-3.pdf. About this Checklist (Continued) Page ii What is the purpose of the CMOM program checklist? This document is a screening-level tool that can help utilities evaluate CMOM programs and identify general areas of strength and weakness. Completing this CMOM assessment will allow the utility to flag CMOM program areas that need improvement and establish priorities for additional, more detailed assessments. In addition, the checklist will allow the utility to compare annual performance (e.g., percent of employees meeting training standards). This document is not intended to be all-inclusive. It addresses the types of practices EPA believes should be considered by most utilities when implementing a CMOM program. However, the ways in which utilities use the information gathered through the checklist will depend on the complexity and site- specific issues facing individual collection systems. When reviewing the questions, utilities should use their judgment to determine if the question is reasonable for their collection system size and design. How do I use this checklist? The questions on the checklist will request answer in three different formats: • Check yes, no, or not applicable (N/A) • Fill in the blank, and • Check all that apply. At the end of each section, additional space is provided to allow for comments on or explanations of the answers recorded (information that will be useful to the utility in follow-on planning). Each utility should make an effort to answer all the questions that are applicable to its system. If a particular question takes a significant amount of time to answer, this could be an indication of an area of weakness. Utilities should plan to invest approximately one day to complete the checklist. This document is designed to help utilities perform an initial evaluation of CMOM activities. It is not intended to serve as an absolute indicator of a successful CMOM program, nor will all of the questions apply to every utility. By working through these questions, utilities will be able to identify strengths and areas for improvements for in their CMOM programs. If a utility has a significant number of “no” answers or very few items selected in the checklist, this could indicate an area of weakness. The utility manager then can make a more detailed evaluation, including identifying specific actions needed to address areas for improvement. Page 1 General Information CHECKLIST COMPLETED BY: Date Name Daytime telephone Number UTILITY CONTACT INFORMATION Utility Name: City of Marysville LOCATION: 80 Columbia Avenue Street Address Street Address (continued) Marysville Washington 98270 City State Zip STAFF: Name Title Email Phone ( ) - Fax ( ) - PERMITTED TREATMENT & COLLECTION FACILITIES Permittee/Co-Permittee/Jurisdictions City of Marysville PERMIT COVERAGE WWTP Effluent Collection System Wet-Weather Facility NPDES or State Permit # WA-002249-7 Collection System Description Page 2 SYSTEM INVENTORY # of treatment facilities Conveyance & Pumping Treatment Facilities WWTP design capacity 12.7 Gravity Sewers Force Mains Pump Stations MGD Pipes and pumps Length/quantity 210.5 14 Miles Miles Miles Average daily flow 4.73 MGD Age of system 0 - 25 years old % % % Average dry weather flow 4.16 Percent Percent Percent MGD 26 - 50 years old % % % Percent Percent Percent Access & Maintenance Manholes 51 - 75 years old % % % Number Percent Percent Percent Number of air vacuum relief valves >76 years old % % % Number Percent Percent Percent Number of inverted siphons _____________________ Service Area Characteristics Service area 6,050 Number of Service Connections ACRES Residential Commercial Industrial TOTAL 15,103 + 860 + = 15,963 Service population 53,203 NUMBER NUMBER NUMBER NUMBER PEOPLE Annual precipitation 42± INCHES At main line connection only Beyond porperty line/clean out From main line to property line or easement/cleanout Other: ________________________________ Combined Sewer Systems What percent of sewer system is served by combined sewers (i.e., sanitary sewage and storm water in the same pipe)? 0% PERCENT 1 Number Collection System Description Page 3 Gravity Sewers Force Mains PIPE DIAMETER 8 inches or less* 66% % PERCENT PERCENT 9 - 18 inches 27% % PERCENT PERCENT 19 - 36 inches 6% % PERCENT PERCENT >36 inches 2% % PERCENT PERCENT *Assumed <6 = FM. Also, approx. 2% unknown PIPE MATERIALS Prestressed concrete cylinder pipe (PCCP) % % PERCENT PERCENT High density polyethylene (HDPE) 0.3% % PERCENT PERCENT Reinforced concrete pipe (RCP) 0.2% % PERCENT PERCENT Polyvinyl chloride (PVC) 74% N/A PERCENT PERCENT Vitrified clay pipe (VCP) 0.5% N/A PERCENT PERCENT Ductile iron 0.8% % PERCENT PERCENT Non-reinforced concrete pipe 15% % PERCENT PERCENT Asbestos cement pipe 0.1% % PERCENT PERCENT Cast iron 0.04% % PERCENT PERCENT Brick % % PERCENT PERCENT Fiberglass % % PERCENT PERCENT Other (Explain) Unknown 8.4% % PERCENT PERCENT Engineering Design (ED) Page 4 ED-01 Is there a document, which includes design criteria and standard construction details? Yes No ED-02 Is there a document that describes the procedures that the utility follows in construction design review? Yes No ED-03 Are WWTP and O&M staff involved in the design review process? Yes No ED-04 Is there a procedure for testing and inspecting new or rehabilitated system elements both during and after the construction is completed? Yes No ED-05 Are construction sites supervised by qualified personnel (such as professional engineers or certified engineering technicians) to ascertain that the construction is taking place in accordance with the agreed upon plans and specifications? Yes No ED-06 Are new manholes tested for inflow and infiltration? Yes No ED-07 Are new gravity sewers checked suing closed circuit TV inspection? Yes No ED-08 Does the utility have documentation on private service lateral design and inspection standards? Yes No ED-09 Does the utility attempt to standardize equipment and sewer system components? Yes No Satellite Communities and Sewer Use Ordinance (SUO) Page 5 SUO-01 Does the utility receive flow from satellite communities? IF NO, GO TO PAGE 6 Yes No SUO-02 What is the total area from satellite communities that contribute flow to the collection system? (Acres or square miles) _________________ SUO-03 Does the utility require satellite communities to enter into an agreement? IF NO, GO TO QUESTION SUO-06. Yes No SUO-04 Does the agreement include the requirements listed in the sewer use ordinance (SUO)? Yes No SUO-05 Do the agreements have a date of termination and allow for renewal under different terms? Yes No SUO -06 Does the utility maintain the legal authority to control the maximum flow introduced into the collection system from satellite communities? Yes No SUO -07 Are standards, inspections, and approval for new connections clearly documented in a SUO? Yes No SUO -08 Does the SUO require satellite communities to adopt the same industrial and commercial regulator discharge limits as the utility? Yes No SUO -09 Does the SUO require satellite communities to adopt the same inspection and sampling schedules as required by the pretreatment ordinance? Yes No SUO-10 Does the SUO require that satellite communities or the utility to issue control permits for significant industrial users? Yes No SUO-11 Does the SUO contain provisions for addressing overstrength wastewater from satellite communities? Yes No SUO-12 Does the SUO contain procedures for the following? (Check all that apply) Inspection standards Pretreatment requirements Building/sewer permit issues SUO-13 Does the SUO contain general prohibitions of the following materials? (Check all that apply) Fire and explosion hazards Corrosive materials Obstructive materials Oils or petroleum Material which may cause interference at the wastewater treatment plant SUO-14 Does the SUO contain procedures and enforcement actions for the following? (Check all that apply) Fats, oils, and grease (FOG) Stormwater connections to sanitary lines (downspouts) Infiltration/Inflow Defects in service laterals located on private property Building structures over the sewer lines Sump pumps, air conditioner connections Organizational Structure (OC) Page 6 OC-01 Is an organizational chart available that shows the overall personnel structure for the utility, including operation and maintenance staff. Yes No OC-02 Are up-to-date job descriptions available that delineate responsibilities and authority for each position? Yes No OC-03 Are the following items discussed in the job descriptions? (Check all that apply) Nature of work to be performed Examples of the types of work Minimum requirements for the position List of licenses required for the position Necessary special qualifications or certifications Performance measures or promotion potential OC-04 What percent of staff positions are currently vacant? % OC-05 On average how long do positions remain vacant? (months) OC-06 What percent of utility work is contracted out? % Internal Communications (IC) Page 7 IC-01 Which of the following methods are used to communicate with utility staff? (Check all that apply) Regular meetings Bulletin boards Email Other (cell phones, radio) IC-02 How often are staff meetings held? (e.g., Daily, Weekly, Monthly, etc.) WEEKLY IC-03 Are incentives offered to employees for performance improvements? Yes No IC-04 Does the utility have an “Employee of the Month/Quarter/Year” program? Yes No IC-05 How often are performance reviews conducted? (e.g., Semi-Annually, Annually, etc.) ANNUALLY IC-06 Does the utility regularly communicate/coordinate with other municipal departments? Yes No Budgeting (BUD) Page 8 BUD-01 What is the average annual fee for residential users? $________________ BUD-02 How often are user charges evaluated and adjusted? (e.g. annually, biannually, etc.) _________________ BUD-03 Are utility-generated funds used for non-utility programs? Yes No BUD-04 Are costs for collection system operation and maintenance (O&M) separated from other utility services such as water, stormwater, and treatment plant? IF NO, GO TO QUESTION BUD-07. Yes No BUD-05 What is your average annual (O&M) budget? $________________ BUD-06 What percentage of the utility’s overall budget is allocated to maintenance of the collection system? $________________ BUD-07 Does the utility have a Capital Improvement Program (CIP) that provides for system repairs/replacements on a prioritized basis? Yes No BUD-08 What is your average annual CIP budget? $________________ BUD-09 What percentage of the maintenance budget is allotted to the following maintenance> Predictive maintenance (tracking design, life span, and scheduled parts replacements) Preventive maintenance (identifying and fixing system weaknesses which, if left unaddressed, could lead to overflows) Corrective maintenance (fixing system components that are functioning but not at 100% capacity/efficiency; for example partially blocked lines) Emergency maintenance (reactive maintenance, overflows, equipment breakdowns) _______________% _______________% _______________% _______________% BUD-10 Does the utility have a budgeted program for the replacement of under-capacity pipes? Yes No BUD-11 Does the utility have a budgeted program for the replacement of over-capacity pipes? Yes No Training (TR) Page 9 TR-01 Does the utility have a formal job knowledge, skills, and abilities (KSA) training program? Yes No TR-02 Does the training program address the fundamental mission, goals, and policies of the utility? Yes No TR-03 Does the utility have mandatory training requirements identified for key employees? Yes No TR-04 What percentage of employees met or exceeded their annual training goals during the past year? _______________% TR-05 Does the utility provide training in the following areas? (Check all that apply) Safety Traffic control Public relations Routine line maintenance Record keeping SSO/Emergency Response Safety Electrical and instrumentation Pump Station operations and maintenance Other Pipe repair CCTV and trench/shoring Bursting CIP TR-06 Are operator and maintenance certification programs used? IF NO, GO TO QUESTION TR-08 Yes No TR-07 Are operator and maintenance certification programs required? Yes No TR-08 Is on-the-job training progress and performance measured? Yes No TR-09 Which of the following methods are used to assess the effectiveness of the training? None Periodic testing Drills Demonstrations TR-10 What percentage of the training offered by the utility is in the form of the following? Manufacturer training ____________% In-house classroom training _____________% On-the-job training ____________% Industry-wide training _____________% Safety (SAF) Page 10 SAF-01 Does the utility have a written safety policy? Yes No SAF-02 How often are safety procedures reviewed and revised? (e.g., Semiannually, Annually, etc.) Yes No SAF-03 Does the utility have a safety committee? Yes No SAF-04 Are regular safety meetings held with the utility employees? Yes No SAF-05 Does the utility have a safety training program? Yes No SAF-06 Are records of employee safety training kept up to date? Yes No SAF-07 Does the utility have written procedures for the following? (check all that apply) Lockout/tagout Biological hazards in wastewater Material safety data sheets (MSDS) Traffic control and work site safety Chemical handling Electrical and mechanical systems Confined spaces permit program Pneumatic and hydraulic safety systems Trenching and excavations safety SAF-08 What is your agency’s lost-time injury rate? % or hours SAF-09 Are the following equipment items available and in adequate supply? (Check all that apply) Rubber/disposable gloves Full body harness Confined space ventilation equipment Protective clothing Hard hats, safety glasses, rubber boots Traffic/public access control equipment Antibacterial soap and first aid kit 5-minute escape breathing devices Tripods or non-entry rescue equipment Life preservers for lagoons Fire extinguishers Safety buoy at activated sludge plants Equipment to enter manholes Fiberglass or wooden ladders for electrical work Portable crane/hoist Respirators and/or self contained breathing apparatus Atmospheric testing equipment and gas detectors Methane gas or optical vector (OVA) analyzer Oxygen Sensors Lower explosion limit (LEL) metering H2S SAF-10 Are safety monitors clearly identified? Yes No Customer Service (CS) Page 11 CS-01 Does the utility have a customer service and public relations program? IF NO GO TO QUESTION CS-03 Yes No CS-02 Does the customer service program include giving formal presentations on the wastewater field to the following? Schools and universities Local officials Media Building Inspector(s) Community gatherings Businesses Citizens Public utility officials CS-03 Are employees of the utility specifically trained in customer service? Yes No CS-04 Are there sample correspondence Q/A’s, or “scripts” to help guide staff through written or oral responses to customers? Yes No CS-05 What methods are used to notify the public of major construction or maintenance work? (Check all that apply) Door hangers Newspapers Fliers Signs Other None Public radio or TV announcements CS-06 Is a homeowner notified prior to construction that his/her property may be affected? Yes No CS-07 Do you provide information to residents on cleanup and safety procedures following basement backups and overflows from manholes when they occur? Yes No CS-08 Does the utility have a customer service evaluation program to obtain feedback from the community? Yes No CS-09 Do customer service records include the following information? (Check all that apply) Personnel who received the complaint or request Name, address, and telephone number of customer Nature of the complaint or request Location of the problem To whom the follow-up action was assigned Date the follow up action was assigned Date of the complaint or request Cause of the problem Date the complaint or request was resolved Feedback to customer Total days to end the problem CS-10 Does the utility have a goal for how quickly customer complaints (or emergency calls) are resolved? IF NO, GO TO THE NEXT PAGE. Yes No CS-11 What percentage of customer complaints (or emergency calls) are resolved within the timeline goals? ___________% Equipment and Collection System Maintenance (ESM) Page 12 ESM-01 Is a maintenance card or record kept for each piece of mechanical equipment within the collection system? IF NO, GO TO QUESTION ESM-03 Yes No ESM-02 Do maintenance records include the following information? (Check all that apply) Maintenance recommendations Maintenance schedule Instructions on conducting the specific maintenance activity A record of maintenance on the equipment to date Other observations on the equipment ESM-03 Are dated tags used to show out-of-service equipment? Yes No ESM-04 Is there an established system for prioritizing equipment maintenance needs? Yes No ESM-05 What percent of repair funds are spent on emergency repairs? ________________% ESM-06 Are corrective repair work orders backlogged more than six months? Yes No ESM-07 Do collection system personnel coordinate with state, county, and local personnel on repairs, before the street is paved? Yes No Equipment Parts Inventory (EPI) Page 13 EPI-01 Have critical spare parts been identified? Yes No EPI-02 Are adequate supplies on hand to allow for two point repairs in any part of the system? Yes No EPI-03 Is there a part standardizations policy in place? Yes No EPI-04 Does the utility have a central location for storing spare parts? Yes No EPI-05 Does the utility maintain a stock of spare parts on its maintenance vehicles? Yes No EPI-06 Does the utility have a system in place to track and maintain an accurate inventory of spare parts? Yes No EPI-07 For those parts which are not kept in inventory, does the utility have a readily available source or supplier? Yes No Management Information Systems (MIS) Page 14 MIS-01 Does the utility have a management information system (MIS) in place for tracking maintenance activities? (Either electronic or good paper files) IF NO, GO TO PAGE 15 Yes No MIS-02 Are the MIS records maintained for a period of at least three years? Yes No MIS-03 Is the MIS able to distinguish activities taken in response to an overflow event? Yes No MIS-04 Are there written instructions for managing and tracking the following information? Complaint work orders Scheduled inspections Compliance/overflow tracking Schedule work orders Sewer System inventory Equipment tools/tracking Customer service Safety incidents Parts inventory Scheduled preventative maintenance Scheduled monitoring/sampling MIS-05 Do the written instructions for tracking procedures include the following information? (Check all that apply) Accessing data and information Updating the MIS Instructions for using the tracking system Developing and printing reports MIS-06 How often is the management information system updated? (Check one) Immediately Within one week of the “incident” Monthly As time permits System Mapping (MAP) Page 15 MAP-01 Are “as-built” plans (record drawings) or maps available for use by field crews in the office and in the field? Yes No MAP-02 Is there a procedure for field crews to record changes or inaccuracies in the maps and update the mapping system? Yes No MAP-03 Do the maps show the date the map was drafted and the date of the last revision? Yes No MAP-04 Do the sewer line maps include the following? (Check all that apply) Scale Street names Pipe material North arrow SSOs occurences/SCOs outfalls Pipe diameter Date the map was drafted Flow monitors Installation date Date of last revision Force mains Slope Service area boundaries Pump stations Manhole rim Property lines Lined sewers Manhole coordinates (GIS) Other landmarks (roads, water Main, trunk, and interceptor sewers Manhole invert elevations bodies, etc.) Manhole and other access points Easement lines and dimensions Distance between manholes Location of building laterals MAP-05 Are the following sewer attributes recorded? (Check all that apply) Size Invert elevations Separate/combined sewers Shape Material Installation date MAP-06 Are the following manhole attributes recorded? (Check all that apply) Shape Depth Age Type (e.g., precast, cast-in-place, etc.) Material MAP-07 Is there a systematic numbering and identification method/system established to identify sewer system manholes, sewer lines, and other items (pump stations, etc.) Yes No Internal TV Inspection (TVI) Page 16 TVI-01 Does the utility have a standardized pipeline condition assessment program? Yes No TVI-02 Is internal TV inspection used to perform condition assessment? IF NO, GO TO PAGE 17 Yes No TVI-03 Are there written operation procedures and guidelines for the internal TV inspection program? Yes No TVI-04 Do the internal TV record logs include the following? (Check all that apply) Pipe size, type, length, and joint spacing Internal TV operator name Distance recorded by internal TV Cleanliness of the line Results of the internal TV inspection (including structural rating) Location and identification of line being televised by manholes TVI-05 Is a rating system used to determine the severity of the defects found during the inspection process? Yes No TVI-06 Is there documentation explaining the codes used for internal TV results reporting? Yes No TVI-07 Approximately what percent of the total defects determined by TV inspection during the past 5 years were the following? Failed coatings or linings % Line deflection % House connection leaks % Joint separation % Illegal connections % Crushed pipes % Pipe corrosion (H2S) % Collapsed pipes % Fats, oil, and grease % Offset joints % Broken pipes % Root intrusions % Debris % Minor cracks % Other % TVI-08 Are main line and lateral repairs checked by internal TV inspection after the repair(s) have been made? Yes No Sewer Cleaning (CLN) Page 17 CLN-01 What is the system cleaning frequency? (the entire system is cleaned every “X” years) __________________ CLN-02 What is the utility’s plan for system cleaning (% or frequency in years)? __________________ CLN-03 What percent of the sewer lines are cleaned, even high/repeat cleaning trouble spots, during the past year? ________________% CLN-04 Is there a program to identify sewer line segments, with chronic problems, that should be cleaned on a more frequent schedule? Yes No CLN-05 Does the utility have a root control program? Yes No CLN-06 Does the utility have a fats, oils, and grease (FOG) program? Yes No CLN-07 What is the average number of stoppages experienced per mile of sewer pipe per year? ________________% CLN-08 Has the number of stoppages increased, decreased, or stayed the same over the past 5 years? Increased Decreased Stayed the same CLN-09 Are stoppages plotted on maps and correlated with other data such as pipe size and material or location? Yes No CLN-10 Do the sewer cleaning records include the following information? (Check all that apply) Date and time Method of cleaning Identity of cleaning crew Cause of stoppage Location of stoppage or routine cleaning activity Further actions necessary/initiated CLN-11 If sewer cleaning is done by a contractor are videos taken of before and after cleaning? Yes No Manhole Inspection and Assessment (MAN) Page 18 MAN-01 Does the utility have a routine manhole inspection and assessment program? IF NO, GO TO QUESTION MAN-06 Yes No MAN-02 Are the results and observations from the routine manhole inspections recorded? Yes No MAN-03 Does the utility have a goal for the number of manholes inspected annually? Yes No MAN-04 How many manholes were inspected during the past year? _________________ MAN-05 Do the records for manhole/pipe inspection include the following? (Check all that apply) Conditions of the frame and cover Presence of corrosion Evidence of surcharge If repair is necessary Offsets or misalignments Manhole identifying number/location Atmospheric hazards measurements Wastewater flow characteristics (flowing freely or (especially hydrogen sulfide) backed up) Details on the root cause of cracks or breaks in Accumulations of grease, debris, or grit the manhole or pipe including blockages Recording conditions of corbel, walls, bench, tough Presence of infiltration, location, and estimated quantity and pipe seals) Inflow from manhole covers MAN-06 Does the utility have a grouting program? Yes No PUMP STATIONS (PS) Page 19 PS-01 Are Standard Operation Procedures (SOPs) and Standard Maintenance Procedures (SMPs) used for each pump station? Yes No PS-02 Are there enough trained personnel to properly maintain all pump stations? Yes No PS-03 Is there an emergency operating procedure for each pump station? Yes No PS-04 Is there an alarm system to notify personnel of pump station failures and overflow? Yes No PS-05 Percent of pump stations with backup power sources 35% PS-06 Does the utility use the following methods when loss of power occurs? (Check all that apply) On-site electrical generators Portable electric generators Alternate power source Other Vacuum trucks to bypass pump station PS-07 Is there a procedure for manipulating pump operations (manually or automatically) during wet weather to increase in-line storage of wet weather flows? Yes No PS-08 Are wet well operating levels set to limit pump start/stops? Yes No PS-09 Are the lead, lag, and backup pumps rotated regularly? Yes No PS-10 Are operation logs maintained for all pump stations? Yes No PS-11 Are the original manuals that contain the manufacturers recommended maintenance schedules for all pump station equipment easily available? Yes No PS-12 On average, how often were pump stations inspected during the past year? Yes No PS-13 Are records maintained for each inspection? Yes No PS-14 Average annual labor hours spent on pump station inspection __________________ PS-15 Percent of pump stations with pump capacity redundancy ________________% PS-16 Percent of pump stations with dry weather capacity limitations ________________% PS-17 Percent of pump stations with wet weather capacity limitations ________________% PS-18 Percent of pump stations calibrated annually ________________% PS-19 Percent of pump stations with permanent flow meters ________________% Capacity Assessment (CA) Page 20 CA-01 Does the utility have a flow-monitoring program? Yes No CA-02 Does the utility have a comprehensive capacity assessment and planning program? Yes No CA-03 Are flows measured prior to allowing new connections? Yes No CA-04 Do you have a tool (hydraulic model, spreadsheet, etc.) for assessing whether adequate capacity exists in the sewer system? IF NO, GO TO QUESTION CA-06 Yes No CA-05 Does you capacity assessment tool produce results consistent with conditions observed in the system? Yes No CA-06 What is the ratio of peak wet weather flow to average dry weather flow at the wastewater treatment plant? 2.5 CA-07 How many permanent flow meters are currently in the system? (Include meters at pump stations and wastewater treatment plants) 8 CA-08 How frequently are the flow meters checked? (e.g. Daily, weekly, monthly, etc.) __________________ CA-09 Do the flow meter checks include the following? (check all that apply) Independent water level Velocity reading Down loading data Checking the desiccant Cleaning away debris Battery condition CA-10 Are records maintained for each inspection? IF NO, GO TO QUESTION CA-12. Yes No CA-11 Do the flow monitoring records include the following? (Check all that apply) Descriptive location of flow meter Frequency of flow meter inspection Type of flow meter Frequency of flow meter calibration CA-12 Does the utility maintain any rain gauges or have access to local rainfall data? Yes No CA-13 Does the utility have any wet weather capacity problems? Trunk F appears to have some problems. Yes No CA-14 Are low points or flood-plain areas monitored during rain events? Yes No CA-15 Does the utility have any dry weather capacity problems? Yes No CA-16 Is flow monitoring used for billing purposes, capacity analysis, and/or inflow and infiltration investigations? Yes No Tracking SSOs (TRK) Page 21 TRK-01 How many SSO events have been reported in the last 5 years? _________________ TRK-02 What percent of the SSOs were less than 1,000 gallons in the past 5 years? ________________% TRK-03 Does the utility document and report all SSOs regardless of size? Yes No TRK-04 Does the utility document basement backups? Yes No TRK-05 Are there areas that experience frequent basement or street flooding? Yes No TRK-06 Approximately what percent of SSOs discharges were from each of the following in the least 5 years? Manholes % Main and trunk sewers % Structural bypasses % Pump Stations % Lateral and branch sewers % TRK-07 Approximately what percent of SSOs discharges were caused by the following in the last 5 years? Debris buildup % Root intrusion % Excessive infiltration and inflow % Collapsed pipe % Capacity limitations % Fats, oil, and grease % Vandalism % TRK-07A What percentage of SSOs were released to: Soil % Basements % Paved areas % Surface water (rivers/lakes/streams) % Coastal, ocean, beaches % TRK-07B For surface water releases, what percent are to areas that could affect: Contract recreation (beaches, swimming areas) % Drinking water sources % Shellfish growing areas % TRK-08 How many chronic SSO locations are in the collection system? __________________ TRK-09 Are pipes with chronic SSOs being monitored for sufficient capacity and/or structural condition? Yes No TRK-10 Prior to collapse, are structurally deteriorating pipelines being monitored for renewal or replacement? Yes No Overflow Emergency Response Plan (OERP) Page 22 OERP-01 Does the utility have a documented OERP available for utility staff to use? IF NO, GO TO QUESTION OERP-04 Yes No OERP-02 How often is the OERP reviewed and updated? (Annually, Biannually, etc.) _________________ OERP-03 Are specific responsibilities detailed in the OERP for personnel who respond to emergencies? Yes No OERP-04 Are staffing continuously trained and drilled to respond to emergency situations? Yes No OERP-05 Do work crews have immediate access to tools and equipment during emergencies? Yes No OERP-06 Does the utility have standard procedures for notifying state agencies, local health departments, the NPDES authority, the public, and drinking water authorities of significant overflow events? Yes No OERP-07 Does the procedure include a current list of the names, titles, phone numbers, and responsibilities of all personnel involved? Yes No OERP-08 Does the utility have a public notification plan? Yes No OERP-09 Does the utility have procedures to limit public access to an contact with areas affected with SSOs? (Procedure can be delegated to another authority) Yes No OERP-10 Does the utility use containment techniques to protect the storm drainage systems? Yes No OERP-11 Do the overflow records include the following information? (Check all that apply) Date and time Location Any remediation efforts Cause(s) How it was stopped Estimated flow/volume discharged Names of affected receiving water(s) Duration of overflow OERP-12 Does the utility have signage to keep public from effected area? Yes No Smoke and Dye Testing (SDT) Page 23 SDT-01 Does the utility have a smoke-testing program to identify sources of inflow and infiltration? Yes No SDT-01A Does the utility have a smoke testing program to identify sources of inflow and infiltration in legal connectors? Yes No SDT-01B Does the utility have a smoke-testing program to identify sources of inflow and infiltration in house laterals (private service laterals)? Yes No SDT-02 Are there written procedures for the frequency and schedule of smoke testing? Yes No SDT-03 Is there a documented procedure for isolating line segments? Yes No SDT-04 Is there a documented procedure for notifying local residents that smoke testing will be conducted in their area? Yes No SDT-05 What is the guideline for the maximum amount of the line to be tested at one time? (Feet or Miles) ___________________ SDT-06 Are there guidelines for the weather conditions under which smoke testing should be conducted? Yes No SDT-07 Does the utility have a goal fro the percent of the system smoke tested each year? Yes No SDT-08 What percent of the system has been smoke tested over the past year? __________________% SDT-09 Do the written records contain location, address, and description of the smoking element that produced a positive result? Yes No SDT-10 Does the utility have a dye-testing program? Yes No SDT-11 Are there written procedures for dye testing? Yes No SDT-12 Does the utility have a goal for the percent of the system dye tested each year? Yes No SDT-13 What percent of the main collection system has been dye tested over the past year? __________________% SDT-14 Does the utility share smoke and dye testing equipment with another utility? Yes No Hydrogen Sulfide Monitoring and Control (HSMC) Page 24 HSMC-01 How would you rate the systems vulnerability for hydrogen sulfide corrosion? (Check only one) Not a problem Only in a few isolated areas A major problem HSMC-02 Does the utility have a corrosion control program? Yes No HSMC-03 Does the utility take hydrogen sulfide corrosion into consideration when designing new or replacement sewers? Yes No HSMC-04 Does the utility have written procedures for the application of chemical dosages? Yes No HSMC-05 Are the chemical dosages, dates, and locations documented? Yes No HSMC-06 Does the utility document where odor is a continual problem in the system? Yes No HSMC-07 Does the utility have program in place for renewing or replacing severely corroded sewer lines to prevent collapse? Yes No HSMC-08 Are the following methods used for hydrogen sulfide control? (Check all that apply) Aeration Chlorine Potassium permanganate Iron salts Sodium hydroxide Biofiltration Enzymes Hydrogen peroxide Other Activated charcoal canisters HSMC-09 Does the system contain air relief valves at the high points of the force main system? Yes No HSMC-10 How often are the valves maintained and inspected? (Weekly, Monthly, etc.) ___________________ HSMC-11 Does the utility enforce pretreatment requirements? Yes No Infrastructure Security Page 25 Although outside the scope of a CMOM program, municipal wastewater utilities should also consider security vulnerabilities. To reduce the threat of both intentional and natural disasters, the utility should take steps to implement appropriate countermeasures and develop or update emergency response plans. APPENDIX H COST ESTIMATES 11/17/2011 WHISKEY RIDGE SEWER EXTENSION PROJECT #S0903 Section Item Description Quantity Units Unit Prices Total Price 1-04.4 1 Minor Change 1 LS $20,000.00 $20,000.00 1-05.5 2 Surveying and As-builts 1 LS $15,000.00 $15,000.00 1-07.15(1)3 SPCC Plan 1 LS $2,500.00 $2,500.00 1-09.7 4 Mobilization 1 LS $68,800.00 $68,800.00 1-10.5 5 Project Temporary Traffic Control 1 LS $15,000.00 $15,000.00 2-01.5 6 Clearing and Grubbing 1 LS $10,000.00 $10,000.00 2-03.5 7 Imported Trench Backfill (Densmore only, top 4' only)2500 TON $15.00 $37,500.00 2-09.5 8 Shoring 1 LS $20,000.00 $20,000.00 4-04.5 9 Crushed Surfacing Base Course (Soper, 87th backfill)1500 TON $30.00 $45,000.00 4-04.5 10 Crushed Surfacing Top Course 100 TON $50.00 $5,000.00 4-06.5 11 Asphalt Treated Base (8" Soper, 8" 87th, 4" Densmore)400 TON $80.00 $32,000.00 5-04.5 12 Planing Bituminous Pavement 3350 SY $4.00 $13,400.00 5-04.5 13 500 TON $95.00 $47,500.00 7-05.5 14 Manhole 54 In. Diam. Type 1 13 EA $5,500.00 $71,500.00 7-05.5 15 Manhole 54 In. Diam. Type 3 1 EA $5,000.00 $5,000.00 7-05.5 16 Manhole Additional Height 56 VF $350.00 $19,600.00 7-05.5 17 Connection to Existing 1 EA $2,000.00 $2,000.00 7-08.5 18 Dewatering 1 FA $50,000.00 $50,000.00 7-08.5 19 Removal and Replacement of Unsuitable Material 250 CY $50.00 $12,500.00 7-17.5 20 Drainage Cutoff Collar 12 EA $2,000.00 $24,000.00 7-17.5 21 PVC Sanitary Sewer Pipe 12" Diam.4300 LF $75.00 $322,500.00 8-01.5 22 Temporary Erosion and Water Pollution Control 1 LS $25,000.00 $25,000.00 8-02.5 23 Property Restoration 1 LS $35,000.00 $35,000.00 8-02.5 24 Wetland Mitigation 1 LS $25,000.00 $25,000.00 8-22.5 25 Restore Pavement Markings 1 LS $5,000.00 $5,000.00 Subtotal Amount $928,800.00 Design and Construction Management $185,760.00 States Sales Tax at 8.6% $79,876.80 Construction Total:$1,194,436.80 HMA Cl. 1/2", PG 64-22 (full overlay Soper Hill Rd and 83rd, partial overlay 87th, half road overlay Densmore) Item Quantity Unit Cost Total 1 Mobilization/Demobilization 1 LS 30,000$ 30,000$ 2 Surveying, Staking and As-Built Dwgs 1 LS 5,000$ 5,000$ 3 Environmental Controls 1 LS 3,000$ 3,000$ 4 Trench Excavation Safety Systems 1 LS 5,000$ 5,000$ 5 Dewatering 1 LS 6,000$ 6,000$ 6 Temporary Bypass Pumping 1 LS 7,000$ 7,000$ 7 Traffic Control 1 LS 6,000$ 6,000$ 8 Locate Existing Utilities 1 LS 3,000$ 3,000$ 9 Removal of Structures and Obstructions 1 LS 16,000$ 16,000$ 10 18" PVC (Including bedding, backfill)510 LF 120$ 61,200$ in improved RoW 510 in unimp easmnt 0 11 48" Precast Manhole (Basic to 8')2 EA 3,500$ 7,000$ 48" Precast Manhole (Height Over 8')14 VF 200$ 2,800$ 12 Connection to Existing Manhole 2 EA 2,500$ 5,000$ 13 Special Excavation of Unsuitable Material 10 CY 35$ 350$ 14 Foundation Gravel 70 TN 20$ 1,400$ 15 Gravel Base (Trench Backfill)1,900 TN 20$ 38,000$ 16 Asphalt Treated Base (Trench Patch 170 TN 100$ 17,000$ 17 Planing Bituminous Pavement 1,000 SY 4$ 4,000$ 18 Hot Mix Asphalt 130 TN 100$ 13,000$ 19 Sawcutting 1,040 LF 3$ 3,120$ Subtotal 233,870$ Contingency (20%)46,774$ Subtotal 280,644$ Sales Tax (8.6%)24,135$ Total 304,779$ Total Construction Cost (Rounded)310,000$ Design, CM, Permitting (30%)100,000$ Total Project Cost (Rounded)410,000$ 71st Street NE Sewer Upsizing - 64th Ave NE to 66th Ave. NE Project SS-D (Basin D6-1) City of Marysville 2011 Sanitary Sewer Comprehensive Plan Preliminary Cost Estimate City of Marysville 2011 Sanitary Sewer Comprehensive Plan Preliminary Cost Estimate Item Quantity Unit Cost Total 1 Mobilization/Demobilization 1 LS 85,000$ 85,000$ 2 Surveying, Staking and As-Built Dwgs 1 LS 16,000$ 16,000$ 3 Environmental Controls 1 LS 10,000$ 10,000$ 4 Trench Excavation Safety Systems 1 LS 16,000$ 16,000$ 5 Dewatering 1 LS 20,000$ 20,000$ 6 Temporary Bypass Pumping 1 LS 40,000$ 40,000$ 7 Traffic Control 1 LS 12,000$ 12,000$ 8 Locate Existing Utilities 1 LS 10,000$ 10,000$ 9 Removal of Structures and Obstructions 1 LS 62,000$ 62,000$ 10 24" PVC (Including bedding, backfill)1,995 LF 165$ 329,175$ in improved ROW 1,195 in unimproved easement 0 11 72" Precast Manhole (Basic to 8')7 EA 8,000$ 56,000$ 12 Special Excavation of Unsuitable Material 600 CY 35$ 21,000$ 13 Foundation Gravel 560 TN 20$ 11,200$ 14 Gravel Base (Trench Backfill)1,600 TN 20$ 32,000$ 15 Asphalt Treated Base-Trench Patch 260 TN 100$ 26,000$ 16 Planing Bituminous Pavement 1,000 SY 4$ 4,000$ 17 Hot Mix Asphalt 230 TN 100$ 23,000$ 18 Sawcutting 4,010 LF 3$ 12,030$ Subtotal 785,405$ Contingency (20%)157,081$ Subtotal 942,486$ Sales Tax (8.6%)81,054$ Total 1,023,540$ Total Construction Cost (Rounded)1,030,000$ Design, CM, Permitting (30%)310,000$ Total Project Cost (Rounded)1,340,000$ Trunk G Rehabilitation - Cedar to Columbia Avenue Project SS-e (Basin CW1) WHISKEY RIDGE AREA SEWER SYSTEM #S0903 Lift Station and Forcemain Section Item Description Quantity Units Unit Prices Total Price 1 Mobilization (8% max)1 LS $49,240.00 $49,240.00 2 Mechanical (Pumps, Piping, Wet Well, Dry Well, Etc)1 LS $250,000.00 $250,000.00 3 Electrical and Instrumentation 1 LS $75,000.00 $75,000.00 4 Structure 1 LS $75,000.00 $75,000.00 5 EG 1 LS $50,000.00 $50,000.00 6 Site Improvements 1 LS $35,000.00 $35,000.00 7 Miscellaneous 1 LS $15,000.00 $15,000.00 8 8" Sanitary Sewer Force Main 1650 LF $70.00 $115,500.00 Construction Subtotal $664,740.00 States Sales Tax at 8.6% $57,167.64 Site Acquisition $100,000.00 Permitting $10,000.00 Survey/Engineering (15%) $99,711.00 Contingency (10%)$66,474.00 Total:$998,092.64 City of Marysville Sewer System CIP West Trunk Pump Station Preliminary Cost Estimate Item Description Quantity Unit Unit Cost Amount 1 Mobilization & Demobilization 1 LS $11,000 $11,000 2 Trench Safety System 1 LS $2,500 $2,500 3 Pump Replacement 3 EA $35,000 $105,000 4 Electrical and Instrumentation 1 LS $30,000 $30,000 Subtotal $148,500 Contingency (20%)$29,700 Subtotal $178,200 Sales Tax (8.6%)$15,325 Total Construction Cost $193,525 Engineering & Administration (15%)$29,029 Total $222,554 Total Project Cost $225,000 City of Marysville Sewer System CIP Cedarcrest Vista Pump Station Emergency Generator Installation Preliminary Cost Estimate Item Description Quantity Unit Unit Cost Amount 1 Mobilization & Demobilization 1 LS $9,000 $9,000 2 Generator 1 EA $100,000 $100,000 3 Electrical 1 LS $10,000 $10,000 4 Site Improvements 1 LS $2,500 $2,500 Subtotal $121,500 Contingency (20%)$24,300 Subtotal $145,800 Sales Tax (8.6%)$12,539 Total Construction Cost $158,339 Engineering & Administration (10%)$15,834 Total $174,173 Total Project Cost $175,000 City of Marysville Sewer System CIP Carroll's Creek Pump Station Emergency Generator Installation Preliminary Cost Estimate Item Description Quantity Unit Unit Cost Amount 1 Mobilization & Demobilization 1 LS $9,000 $9,000 2 Generator 1 EA $100,000 $100,000 3 Electrical 1 LS $10,000 $10,000 4 Site Improvements 1 LS $2,500 $2,500 Subtotal $121,500 Contingency (20%)$24,300 Subtotal $145,800 Sales Tax (8.6%)$12,539 Total Construction Cost $158,339 Engineering & Administration (10%)$15,834 Total $174,173 Total Project Cost $175,000 City of Marysville Sewer System CIP Biosolids Removal Preliminary Cost Estimate Item Description Quantity Unit Unit Cost Amount 1 Permitting and Sampling 1 LS $15,000 $15,000 2 Mobilization and Demobilization 1 LS $50,000 $50,000 3 Dredging and Dewatering 5600 TN $376 $2,105,600 4 Hauling and Land Application 5600 TN $45 $252,000 Subtotal $2,422,600 Contigency (20%)$484,520 Subtotal $2,907,120 Sales Tax (8.5%)$247,105 Total Construction Cost $3,154,225 Engineering & Administration (8%)$252,338 Total $3,406,563 Total Project Cost $3,400,000 City of Marysville Sewer System CIP Screen Replacement for Mechanical Screens Preliminary Cost Estimate Item Description Quantity Unit Unit Cost Amount 1 Mobilization & Demobilization 1 LS $25,000 $25,000 2 1/2-Inch Bar Screen(1)2 EA $150,000 $300,000 Subtotal $325,000 Contigency (20%)$65,000 Subtotal $390,000 Sales Tax (8.6%)$33,540 Total Construction Cost $423,540 Engineering & Administration (15%)$63,531 Total $487,071 Total Project Cost $500,000 APPENDIX I SEPA CHECKLIST !"#$ %&’(&’&)*%&’(’+*)+"",- !" ##"$%&""&$’( )*+ !"##" "$"%"&%’#$""!"%"’"" $%!$%("$%"%!")$! $"%"%""&)$#$$*+" !$+ $$$,-.%*" !"%"#/ 0 *12 - 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2234 2232 4709 2233 2259 2260 1377 3631 3789 2188 2189 1522 17311717175117491729 1748 1746 1745 1743 16881756 1755 17531651 16571665 1671 167316871686 1674 16791685 1684 2335 2074 2068 2067 2065 2069 2117 2063 2062 63356334 205320492054 2045 2046 2281 205522822044 1659 1663 1661 2034 19991998 1994 1995 1992 1993 375937583757 3756 2030 3754 3753 376019731972 1950 1965 2019 1964 3801 3705 3802 3608 1298 1313131213111305 12971296 3657 36583659 3669 3672 3676 1226 1225 1224 1223 3711 1306 1307 1308 1310 1323 1270 1322 1320 1319 1318 4872 3812 1274 1265 3720 37173721 100310041005 1006 1007 1012 1008 1167 11661165 1072 1074 1088 1071 1602 1603 1606 2002 2001 2000 2036 2037 2038 3735 3736 3733 1923 1924 37322010 2011 2009 2008 2007 1169 1942 1608 1609 15911593 12291209 12101211 121212131214 1215 12161335 1336 1337 3689 3690 3691 1338 3692 3694 3695 3367 3696 3697 3700 3699 36983380 3379 3378 3377 33063307 1821 1857 1840 1839 1838 1800 1850 1851 1852 1805 1389 1380 13781376 1377 1383 1384 13851387 1386 2764 1765 1766 1775 2550 25482549 248225462522 2523 2526 2527 2521 2515 2518 2520 2510 2519 2509 3308 33093310 3399 3400 34013402 3398 3397 3295 3294 3293 3383 3382 386738683594 387035913575 3574 3585 3583 3582 3579 357735783551 4730 4595 4716 4089 1357 1362 1367 1369 3581 1366 3876 2475 2476 2478 2534 2535 2537 2538 2539 2543 2542 2541 2540 1563 1564 1565 1566 1567 1568 1501 1502 1503 1504 1505 15131554 1555 1556 1557 3781 153915381537 1859 1846 1858 1845 18441843 1828 1829 3782 1842 1813 1818 1819 JUNCTION 45 217 534 803 791 790 669 430 429 4707 4706 4705 23452407 2703 2720 3058 2914 2893 2880 2999 5936 2785 3000 5934 5930 2942 29582959 3610 3081 5925 2865 1422 2425 21982199 2300 2307 3632 1523 1754 1672 2066 1658 1997 2031 3607 3656 3677 1269 1010 1605 3734 1943 3366 3376 3375 1849 1856 1834 32973296 3590 4607 1508 1542 1841 1814 1820 MARYSVILLE WEST P.S. ASH AVE. P.S. QUIL CEDA GLEN P.S. REGAN ROAD P.S. 3RD STREETP.S. EAGLE BAY P.S. WATERFRONT PARK P.S. SUNNYSIDE P.S. WEST TRUNK P.S. SOPER HILL P.S. 51STAVE. P.S. 88TH STREET P.S. KELLOGG RIDGE P.S. CARROLL'S CREEK P.S. CEDAR CREST VISTA P.S. MOUNTAIN VIEW SHORES P.S. F22 (FUTURE) A24 (FUTURE) F13 (FUTURE) A16 (FUTURE) CE5-7 G7 CW1 D3-5 D6-2 CW15 F22-1 A6 G3 F13-1 B1 D3-12 A25-1 A19 D10-2 G1 D10-6 A24-5 CW11-1 F4 D6-5 A21 F21 F20 A26 F12 D1 F22 D10-3 F14 A20 A23 A10 A16 D10-4 A7 D3-11 G2 F5 D6 A15 G4 G8 A13 A25 A22 D10-1 F15 D3-8 D9 F13 CE5-3 (FUTURE) F10 B2 D12 D3 D5 A24 A18 CW3 A28 F7 D3-1 F13-2 A27 A24-4 A8 A17 CW11 CE5-2 A5 D3-4 A18 (FUTURE) A24-2 A24-3 D3-10 B3 D3-9 D5-2 CE5 CE7 CE6 G5 CW7 D3-6 F16 A12 F2 D3-13 CW2 F3 F17 CW14 F9 A24-1 CW8 D3-3 B5 G6 F19 D4 D6-4 CE5-3CE2 CW12 A2 CW10 A16-1 A9 CW4 F8 A12-2 D3-7 D3-2 D2 D10-5 A4 F18 F11 CE3 B4 D8 D9-1 D10 A1 A18-3 (FUTURE) A18-1 CE5-1 A11 A12-3 D5-1 D11 A14 CE9 D6-3 A18-3 CE5-4 CW9 D7-2 CW5 F1 A12-4 CE8 CE4 D6-1 A12-1 F6 D7-1 CE5-5 CW6 CW13 D7 CE1 A18-2 CE5-6 LEGEND: !MODELED MANHOLES MODELED SEWER LINES DIAMETER 8" 10" 12" 14" 15" 16" 18" 21" 24" 27" 30" 36" 42" 48" FORCEMAIN MODELED SUB-BASINS BASINS: BASIN A BASIN B BASIN C EAST BASIN C WEST BASIN D BASIN F BASIN G CITY OF MARYSVILLE SEWER COMPREHENSIVE PLAN EXHIBIT III: MODELED SEWER LINES, MANHOLE ID'S AND BASINS CONSULTING ENGINEERSM:\MARYSVILLE\11447_Sewer_Comp_Plan\Figures\Ex III SUBBASINS-MODELED-MH-ID24x36.mxdµ 0 1,800 3,600900 Feet SCALE 1" = 1800' ! ! ! ! !!!! ! !! ! ! ! !! ! ! !!!!! ! ! ! !!!!!!!! ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! ! ! ! ! !! !! ! ! !!! !! !! ! !!! ! ! ! ! ! !! ! !! ! ! ! ! ! ! ! ! ! !!!! ! ! ! ! !! ! ! ! ! ! ! !! ! ! !! ! ! ! ! !! ! !! ! ! !! !! !!!!!! !!! ! ! ! ! ! ! ! ! ! !!! !!!!!!! ! ! ! ! ! ! ! ! ! ! ! ! !!! !!!!! ! ! ! ! ! !!! ! ! !!!! ! !!!! ! !! ! !!!!!! !! ! !!!! !!!!!!! ! ! ! ! !!! ! ! ! ! ! ! ! !!!!! !! !!!! !! ! ! !! ! ! ! ! ! ! ! ! !! ! ! !!!!!!!!!!!!!!!!!!! ! ! ! ! ! !! !! ! !!!!! !!! !!!!!!!! ! ! ! !!!!!! !!! ! !!!!!! ! !!!!!!!!! !! ! ! !! !!! !!!! !!!! !!!!! !!!! ! ! ! ! ! ! !! ! ! ! ! ! !! ! ! ! ! !!! !!!!!! ! ! ! !!! ! !!! ! !! ! ! ! ! ! ! !! !!!!!! ! ! ! !!!!!! ! !! ! !! !!!!!!!! ! ! !!!! ! !!!!!!!!! !!! !!! ! !!! !! !! ! ! !! !!! ! ! ! !! ! !!!!! !!!!!!!!!!!!!!!!!!! !! ! !!!!! 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45291222824462895 4275 52982537178344386486650466524999 18052182 258138434434 33143204 346344286601 27795010 12 1 5 16784206 6602 5837 5839 6 6 2 93203418445753850 167516801564 4294 52512444 961249542889123209 3202 2396192031936279 3572 4296 4295 918 35053875 4555 3883 4436425228946505 16792950 1 2 6 0209144805981 1473 12 2 1 4839 5831 2616 1937 238811996 58 4 2 96549713170 12251897 47274273 5853 719473025542213 61868636844 6642 1918 23244180 3412M 193015376788 27892404 2417 65434067 1 2 5 6 139 3186 11994190945615005 598635193975 16773 0 5 6 4997 4 7 9 7 2926 2096 4684237044261262433943964573 473249936780 178761665333332 15211 2 7 23978 4800 4844 443114706515 6865 2312468635 1 8 111994962 57371 2 8 959893923 128 2448 3428 2644 3467166936379152057 48124190 919 716 2199 2069 6933510942923943121013 6 8 2028 15465242 6938 5310 4332 157530556797 3568 5094 5236 68622804173816032471058403419754023 584 32328254034563514 26212612 2384 1 5 4 319774253048376424116 6520 39673154 4244 19794102 3242 3845 5849 4263 6754 2546 4091 5255 363513 3 171 3980 2671118 3974 6277 2488 3161208 3916 35072490 2636 3007 6514 11201 1267 4082 4682 4 8 8 7 5228 1539 1280 1276 7446 2197 475668606655653664661 1929100743933582439034584179 49606929319151049612097 7186845 51471080117 1 3 263110793 595146769261080240886846 5008 2895000 4841 1974 1 0 7 1822 10794 852 21832494 1 4 6 1 215 4967 123042614440437 58444437684765061981 4935 221044795838427451592014 3949 472959833612 3300 4066 2387 2220 352049953057 957 477335063334 4840 3041 10799 4 8 8 8 2569 3907 6489 662 2343 232715192948 46831921 16762368 305210800 515449665840 4726 4850 363641892056480912 2 3 6632 169946855854 64874306 5841 3957 47 96 12835584148 3 4 1 4 1369 3881 5156 279840254150 1894 3800 4151 3958 701 1622897 921 294972 1819 46221707 1 2 7 7686019336278 16703401 5309 4 7 9 5 8535 5004 2371 5911563 1148 3001 1041 351639721232 6864 4663 663039264340 4399 124121124448 35 1 3 448110791 5007 3942 2198 13219782389 25881860 39795239 23974826430951211976 2189 414942584338 2790 39774209 4998 3910444542851 7 2 6939 10787 4331 4975 4256 28545012 2635 4110 221810574581 1674127 2622472865341934 1212 3834 1936 21106432420 117 2547 3042 16672543 40844246 2533 38042572 15 3 8 5095 585010789 3194 3418 3243 3285168 1279 1900 2632 3508 3915 2613 350 9 2385 129 0 6174113 2070 4882 6940 2181 2801 71240795253914433624454836 1013 1468 5256 40223924 377 3984 2633 1672 4262 32114804219040202991 28503803 52354558 4031 4718641 119 65416654 1596544 6801 3922 2415 5243 6937 1211 10798 472011198 6784 2358 2553 5254 4890 164 3417 1574 29004249 6848 2549 2418 5227 3053 59634805 3187 2800 6793 120 150668616794 3981 2406 23235988 2544 34 1 3 2995 2405 30661271 11995 4065 1149 6785 3205 4963 66433301 2896 2491 1544 6276 3271 6783 11200 1275 6633 4811 1209 3380 6644 4121 5115 6518 597259764824 379 4725 27616537 1270 5111 1665 209459754265 1469 5013 5738 1266 10792 5060 2211 4799 64885317 6756 38523430 3335 4301 1917 10113976 4078 2407 5304 1666 4230 2634 2571 4801 4790 1507 3006 2214 4101 2098 6494 12294442 4803 10788 2802 16713184 122045602568 4127 5138 4792 4400 2580 4556 6757 7441 3036 2414 553 2901 3088 1471 4802 3973 23902386 6755 19 8 0 4934 5119 4968 5962 3315 3245 4083 51035995 56875993 4312 3195 2221 920 4030 190 2195 643617373197 6631 5116 5851 4145 6603 1364 4637 1114 6536 5303 1481 4392 2209 3884 4280 2534 3427 5114 3185 5848 6653 4842 6770 114553 2119 4064 4279 4112 6596 6275 1115 3844 6604 2398 2099 1240 1627 1116 5234 6522 5231 4877 623 665 10797 4746 6493 2951 5302 4747 6931 1119 6930 10796 3208 1118 10786 3201 1051 3786 31805600 11997 10804 6925 1117 3153 2212 10803 MARYSVILLEWEST P.S. ASH AVE. P.S. QUIL CEDA GLEN P.S. REGAN ROAD P.S. TO WWTP 3RD STREET P.S. EAGLE BAY P.S. WATERFRONT PARK P.S. SUNNYSIDE P.S. WEST TRUNK P.S. SOPER HILL P.S. 51ST AVE. P.S. 88TH STREET P.S. KELLOGG RIDGE P.S. CARROLL'S CREEK P.S. CEDAR CREST VISTA P.S. MOUNTAIN VIEW SHORES P.S. F22 (FUTURE) A24 (FUTURE) F13 (FUTURE) A16 (FUTURE) CE5-7 G7 CW1 D3-5 D6-2 CW15 A6 F22-1 G3 B1 F13-1 A25-1 D3-12 A19 D10-2 G1 D10-6 A24-5 A21 CW11-1 F4 D6-5 F21 A26 F20 F12 D1 F22 D10-3 A20 F14 A23 A10 A16 A7 D10-4 A15 G2 A13 F5 D6 A25 D3-11 A22 G4 G8 D10-1 F15 D3-8 D9 B2 F13 CE5-3 (FUTURE) F10 D12 A24 A18 D3 A28 D5CW3 A27 F7 D3-1 F13-2 A8 A24-4 A17 A5 CE5-2 CW11 A24-2 B3 D3-4 A24-3 A18 (FUTURE) D3-10 D3-9 D5-2 CE5 CE7 A12 CE6 G5 CW7 D3-6 F16 F2 D3-13 CW2 F3 B5 A24-1 F17 CW14 F9 CW8 D3-3 G6 F19 D4 D6-4 A2 CE5-3CE2 CW12 A9 A16-1 CW10 CW4 A12-2 F8 D3-7 D3-2 D2 A4 D10-5 CW6 B4 F18 CE3 A1 D8 D9-1 F11 D10 A18-1 A18-3 (FUTURE) CE5-1 A12-3 A11 D5-1 CW13 A14 D11 D7 CE9 D6-3 A18-3 CE5-4 CW9 D7-2 CW5 A12-4 F1 CE8 CE4 D6-1 CE1 A12-1 F6 D7-1 A18-2 CE5-6CE5-5LEGEND: !MODELED MANHOLES PIPE DEFFICIENCIES 2011 PIPE DEFFICIENCIES 2017 PIPE DEFFICIENCIES 2031 MODELED SEWER LINES DIAMETER 8" 10" 12" 14" 15" 16" 18" 21" 24" 27" 30" 36" 42" 48" "PUMP STATIONS FORCEMAIN MODELED SUB-BASINS BASINS: BASIN A BASIN B BASIN C EAST BASIN C WEST BASIN D BASIN F BASIN G CITY OF MARYSVILLE SEWER COMPREHENSIVE PLAN EXHIBIT IV: PIPE ID AND CAPACITY DEFFICIENCIES (MODEL RUNS 2011, 2017 AND 2031) CONSULTING ENGINEERSM:\MARYSVILLE\11447_Sewer_Comp_Plan\Figures\Ex IV PIPE_DEFFICIENCIES3_24x36.mxdµ SCALE 1" = 1800' 0 1,800 3,600900 Feet " " " " " " " " " " " " " " " " " " " " PROPOSED PUMP STATION 4,200 GPM(BUILDOUT) PROPOSED PUMP STATION 3,076 GPM (BUILDOUT) 36"24"24" 15" 20" FM 12"18"18"18"18" FM18" 21" QUIL CEDA GLEN 15"18"12"10"10"10"8"8"8"8"8"8"8"4" FM 8"8"8"8"PUMP STATION 200 GPM12"12"18"24" 1 0 "10"10"PROPOSED PUMP STATION 300 GPM 152ND TRUNK - 51ST TO THE EAST (2028) PS-B (2006) PS-A (2010) PUMP STATION REHAB. (2020) PS-D (2005) PS-C (2008) PS-E (2007) MOUNTAIN VIEW SHORES PUMP STATIONUPSIZING (2020)8"LAKEWOOD SEWER EXTENSION (2018)--12"15"18 " -------------------------------- 30 24 12184842423018 12"30"15"30"30"-14 -1018 101818 12 -8"--8"--88TH ST. NE AT ALLEN CREEK (2022) CIP SS - D (2015) SUNNYSIDE BLVD (FROM 53RD AVE NE TO 60TH DR. NE) (2024) CIP SS - E (2016) CIP SS - C (2012) 169TH PL. NE AND 277TH PL. NE (2026) CARROLL'S CREEK P.S. MOUNTAIN VIEWSHORES P.S. 51ST AVE. P.S. KELLOGG RIDGE P.S. 88TH STREET P.S. CEDAR CREST VISTA P.S. MARYSVILLE WEST P.S. ASH AVE. P.S. QUIL CEDA GLEN P.S. 3RD STREET P.S. EAGLE BAY P.S. WATERFRONT PARK P.S. SUNNYSIDE P.S. REGAN ROAD P.S. SOPER HILL P.S. WEST TRUNK P.S.67TH51STI-583RDSR 964TH 108TH STATE3RDGROVE 87TH100TH 152NDBURLINGTON NOR TH ERN 84TH 60TH200TH 44TH19THSR531 4TH 71ST188TH 11TH23RD2NDCEDAR77THBEACHSUNNYSIDE136TH 132ND 7TH 55TH148TH WADE 79TH25THMC RAE 156TH MARINE 76THRAILROAD112TH 93RDTWIN LAKESQUINN40TH56TH58TH86TH43RD140THSMOKEY POINT59TH46THUNIONF O R T Y F I V E 74TH 36TH21ST62NDDENSMORE11TH AVE NEF O R T Y F I V E R O A D 123RD15TH 47TH138TH 142ND 81ST1ST 168TH 50TH9TH95TH 143RD 41ST20TH94TH DELTAPACIFICSHOULTES 119TH 61ST17TH69TH57TH49TH 35TH 96THHILLTOP 144TH 98TH 72ND 104TH 113TH5TH 31ST8TH92ND 128TH 158TH 53RD26TH166TH 6TH 73RD10TH182ND 176TH 75TH66TH121ST 88TH 109TH 97TH 116TH 157TH 155TH 45TH103RD54TH164TH 1 6 2N D MAPLE LAKEW O O D COLUMBIA48THOLD TULALIP18TH135TH 165TH 151ST 110TH 169TH27TH 63RD174TH SR 529129TH MC PHERSON 89TH39TH180TH37TH134TH 33 R D 16TH106TH ALDER68TH 179TH 194TH 105TH 65TH80TH 30T H 124TH 120TH 107TH 172ND ST NW 85TH38TH192ND 141ST 131ST 70TH2 2 ND 198TH 90TH 189TH 127TH 78TH 29TH52ND122ND 118TH 133RD 91ST 178TH 101ST 150TH 139TH SUN N Y S I D E S C H O O L 125TH 184TH JOHNSON TRACTS LA K E W O O D R O A D 102ND 177TH 161ST LIBERTY 175TH SOPER HILL 99THMERIDIAN 42NDQUIL SCENIC111TH 115TH 82ND 15 3 R D SHORT 170TH 130TH146TH173RD 171ST 145TH HIGHLAND126TH PARKSIDE 147TH34TH KIMBERLY117TH HILAND VIEW ARMAR SUNNY RIDGE 160TH STURGE O N WEST F O R K Q U I L C E D A C R JUDSONSPRING LANEMANORTOTEM PARK 28THWILDWOOD 58TH 119TH 129TH 20TH49TH26TH39TH83RD39TH95TH 74TH88TH 77 T H 5 9 TH 72ND 10TH 60TH47TH99TH 49TH108TH 70TH72ND 128TH 54TH44TH71ST 67TH 47TH132ND 58TH84TH 48TH91ST31ST 69TH90TH 53RDALDER99TH58TH 55TH58TH33RD44TH76TH 104TH 70TH 140TH 7 6 T H 54 T H 30 TH77TH81ST71ST6TH45TH130TH59TH65TH 110TH 44TH55TH38TH63RD77T H 126TH 66TH 57TH46TH 60TH 67TH 126TH 54TH52ND47TH179T H 36TH54TH49TH43RD170TH 54 T H 54TH60TH 88TH 107TH33RD 71ST68TH169TH 56TH120TH 47TH44TH40TH 126TH 70TH 72ND69THSMOKEY POINT72ND69TH 130TH 83RD49TH66TH61ST 90TH 135TH 57TH54TH58TH 7 3RD78TH 10TH 78TH39TH57TH68TH127TH 134TH 38TH58TH42ND188TH 56TH 129TH 75TH2ND87TH27TH 55TH51ST82ND 97TH 36TH57TH5TH42ND68TH38TH52ND74TH 65TH 73RD75TH55TH25TH 64TH178TH 70TH 54TH41STSR531 52ND36TH52ND81ST43RD78TH 87TH46TH70TH162ND 66TH11TH67TH 74TH124TH 58TH79TH 71ST5TH66TH 98TH DELTA118TH 47TH17 T H 121ST 1 22ND 75TH 63RD48TH 60TH 92ND 54TH66TH75TH 177TH 75TH 67TH77TH60TH79TH40TH84TH 105TH 74TH162ND 72ND50TH 70TH44TH57TH103RD 57TH 63RD52ND 49TH 6TH 56TH55TH56TH 140TH 48T H 81ST 71ST40TH 66TH69TH54TH93RD57TH128TH 109TH 68TH180TH 55TH59TH70TH74TH43RD77TH 146TH 126TH 46TH29 T H 73RD58TH58TH50TH52ND121ST 79TH55TH96TH 76TH136TH 42ND52ND49TH125TH 6 1S T 85TH42ND 55TH 67TH41ST48TH128THCOLUMBIA95TH 175TH 55TH135TH 23RD57TH46TH44TH91ST JOHNSON TR A C T S I-555TH56TH53RD53RD49TH36TH37TH27TH 74TH42ND28TH 86TH45TH 135TH 81ST50TH134TH123RD 69TH72ND65TH 178TH 46TH 91ST 178TH 132ND31ST 101ST 177TH 61 S T55TH156TH38TH 88TH 81ST 146TH 76TH64TH62 N D54TH85TH 72N D 65TH61ST56TH55TH51ST48TH92ND 81ST 122ND HILLTOP 73 R D 57TH51ST 49TH 103RD 58TH97TH 79TH133RD 73RD52ND72ND 89TH 76TH 75TH56TH99TH 70TH 121ST43RD23RD49TH 142ND 95TH 73RD125TH83RD86TH176TH 64TH140TH 121ST 47TH55TH 107TH 120TH 64TH73RD 140TH 68TH 56TH 69TH44TH71ST45TH145T H 83RD31ST56TH79TH38TH158T H 55TH95TH 63RD69TH 63RD 65TH65TH 122ND 105TH 61ST74TH 25TH 45TH57TH54TH72ND 78TH47TH 69TH19TH71ST 98TH 8TH 19TH120TH 49TH48THBURLINGTON NORTHERN156TH 72ND57TH49THBURLINGTON NORTHERN144TH 50TH2ND46TH55 T H 38TH 148TH 69TH 106TH 38TH72ND180TH 66TH 10 3 R D29TH 40TH51ST 77TH103RD 52ND102ND 75 T H 96TH 134TH 143RD 75TH77TH 44TH126TH 62ND70TH55TH95TH 11TH 66TH73RD 78TH74TH65TH 176TH 67T H48TH67TH 128TH 33RD11TH58TH59TH57TH45TH62ND69TH73RD68TH100TH57TH89TH52ND52ND76TH 176TH 67TH 61ST59TH 133 R D 45TH53RD 75TH138TH 67TH 177TH 42ND133RD 91ST 73RD72ND 52ND 9TH 107TH 51ST78TH64TH75THSR 9129TH 59TH75TH54TH179TH 96TH 46TH113TH 54TH93RD 97TH 104TH39TH 92ND21ST 1ST 61ST70TH3RD27TH 68TH 98TH19TH 80TH 65TH80TH 53RD52ND98TH 141ST 34TH 44TH46TH76TH 142ND 59TH59TH45TH47 T H 108TH 62ND49TH76TH 57TH 2ND 72ND99TH 52ND61ST57TH 116TH 90TH 75 TH 66TH 55TH52ND38TH132ND 70TH70TH156TH62ND88TH44TH 60TH168TH 69TH48TH60T H56TH47TH5TH 144TH ALDER40TH62ND 69TH 110TH 77 TH 134TH 52NDCITY OF MARYSVILLE SEWER COMPREHENSIVE PLAN EXHIBIT V: MODELED SEWER LINES W/ IMPROVEMENTS AND BUILDOUT CONDITIONS M:\MARYSVILLE\11447_Sewer_Comp_Plan\Figures\Ex V impvts and buildout- 24x36.mxdµ 0 1,900 3,800 5,700950 Feet SCALE 1" = 1900' LEGEND: "LIFT STATIONS "PROPOSED PUMP STATION PROPOSED AND CIP PROJECT 6" FM 8" 10" 12" 15" 18" 20" 21" 24" 27" 30" 36" FORCE MAIN 6 YEAR CIP PIPELINE IMPROVEMENTS 20 YEAR CIP PIPELINE IMPROVEMENTS (2017-2031) BUILDOUT PIPELINE SURCHARGES (After 2031) !PROPOSED MANHOLE !MODELED MANHOLES MODELED SEWER LINES SIZE EXISTING: 8" 10" 12" 14" 15" 18" 21" 24" 27" 30" 36" 42" 48" !EXISTING MANHOLE EXISTING SEWER LINES MARYSVILLE CITY LIMITS PARCELS BASIN A BASIN B BASIN C EAST BASIN C WEST BASIN D BASIN F BASIN G " " " " " " " " " " " " " " " " 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4934 5119 4968 5962 3315 3245 4083 51035995 56875993 4312 3195 2221 920 4030 190 2195 643617373197 6631 5116 5851 4145 6603 1364 4637 1114 6536 5303 1481 4392 2209 3884 4280 2534 3427 5114 3185 5848 6653 4842 6770 114553 2119 4064 4279 4112 6596 6275 1115 3844 6604 2398 2099 1240 1627 1116 5234 6522 5231 4877 623 665 10797 4746 6493 2951 5302 4747 6931 1119 6930 10796 3208 1118 10786 3201 1051 3786 31805600 11997 10804 6925 1117 3153 2212 10803 ASH AVE. P.S. REGAN ROAD P.S. MARYSVILLE WEST P.S. QUIL CEDA GLEN P.S. EAGLEBAY P.S. 3RD STREET P.S. TO WWTP WATERFRONT PARK P.S. SUNNYSIDE P.S. WEST TRUNK P.S. SOPER HILL P.S. 51ST AVE. P.S. 88TH STREET P.S. KELLOGG RIDGE P.S. CARROLL'S CREEK P.S. CEDAR CREST VISTA P.S. MOUNTAIN VIEW SHORES P.S. A24 (FUTURE) F22 (FUTURE) F13 (FUTURE) A16 (FUTURE) CE5-7 G7 CW1 D3-5 D6-2 CW15 A6 F22-1 G3 B1 F13-1 A25-1 D3-12 A19 D10-2 G1 D10-6 A24-5 CW11-1 A21 F4 D6-5 F21 A26 F20 F12 D1 F22 D10-3 A20 F14 A23 A10 A16 A7 D10-4 D3-11 A15 G2 A13 F5 D6 A25 A22 G4 G8 D10-1 F15 D3-8 D9 B2 F13 CE5-3 (FUTURE) F10 D12 A24 A18 D3 A28 D5CW3 A27 F7 D3-1 F13-2 A8 A24-4 A17 A5 CW11 CE5-2 A24-2 B3 D3-4 A24-3 A18 (FUTURE) D3-10 D3-9 D5-2 CE5 CE7 A12 CE6 G5 CW7 D3-6 F16 F2 D3-13 CW2 F3 B5 A24-1 F17 CW14 F9 CW8 D3-3 G6 F19 D4 D6-4 A2 CE5-3CE2 CW12 A9 A16-1 CW10 CW4 A12-2 F8 D3-7 D3-2 D2 A4 D10-5 CW6 B4 F18 F11 CE3 A1 D8 D9-1 D10 A18-1 A18-3 (FUTURE) A11 CE5-1 A12-3 D5-1 D11 CW13 A14 D7 CE9 D6-3 A18-3 CE5-4 CW9 D7-2 CW5 A12-4 F1 CE8 CE4 D6-1 CE1 A12-1 F6 D7-1 A18-2 CE5-6CE5-5 LEGEND: !MODELED MANHOLES MODELED SEWER LINES SIZE 8" 10" 12" 14" 15" 18" 21" 24" 27" 30" 36" 42" 48" FORCEMAIN LOW VELOCITY (<2FT/S) IN 2011 MODELED SUBBASINS BASINS: BASIN A BASIN B BASIN C EAST BASIN C WEST BASIN D BASIN F BASIN G CITY OF MARYSVILLE SEWER COMPREHENSIVE PLAN EXHIBIT VI: PIPE ID AND PIPELINE VELOCITY DEFFICIENCIES (2011)M:\MARYSVILLE\11447_Sewer_Comp_Plan\Figures\ Ex VI PIPE DEFFICIENCIES_24x36.MXDµ 0 1,900 3,800950 Feet SCALE 1" = 1800' SUMMARY: TOTAL LENGTH OF MODELED PIPE = 318,770 LF LENGTH OF PIPE WITH VELOCITY LESS THAN 2 FPS = 153,710 LF LENGTH OF PIPE WITH VELOCITY LESS THAN 1 FPS = 21,758 LF