Chapter 2 Treatment Facility Menus



Similar documents
Biofiltra on: West Hylebos Log Yard

The International Stormwater BMP Database Part 1: Summary of Database

Contech Engineered Solutions LLC Subject: Comments on Tentative Order R XXXX, NPDES No. CAS612008

Low Impact Development

Improper storage of fuel on construction sites will increase the risk of water pollution that may occur as a result of leaks or spills.

Massachusetts Department of Environmental Protection Bureau of Resource Protection - Wetlands Program Checklist for Stormwater Report

AquaPaver & SF-Rima Permeable Interlocking Concrete Pavers

Improper storage of potential pollutants will increase the risk of water pollution that may occur because of spills.

PROPRIETARY WATER QUALITY PRODUCTS AND THE METROPOLITAN ST. LOUIS SEWER DISTRICT S STORMWATER MANAGEMENT PROGRAM

SUSTAINABLE URBAN DRAINAGE SYSTEMS

National Pollutant Removal Performance Database

Field Performance of Two Stormwater Bioretention Filtration Design Configurations

How To Test A Stormwater Treatment System

Lessons Learned from the Expert BMP Panel Process That May Apply to MTDs. Tom Schueler Chesapeake Stormwater Network

Scheduling Maintenance for Infiltration Basins and Trenches

POLLUTION PREVENTION FACT SHEETS: CATCH BASINS. Description

Use of Green Roofs to Meet New Development Runoff Requirements. Greg Davis Nov. 8, 2007

Permeable Pavement Treatment Capacity

Interlocking Concrete Pavement Institute (ICPI) Model Stormwater Ordinance for Permeable Interlocking Concrete Pavements August 2010

DESCRIPTION OF STORMWATER STRUCTURAL CONTROLS IN MS4 PERMITS

City of Lakeland s Wetlands Treatment System An Overview

Total Suspended Solids: The Hows & Whys of Controlling Runoff Pollution

Pervious Pavers. By: Rich Lahren. Hebron Brick & Block Supply

Storm Water Runoff. Managing. A Self-Assessment Guide for Wisconsin Businesses. Storm water runoff is coming. This guide provides businesses

Detention Ponds. Detention Ponds. Detention Ponds. Detention Ponds. Detention Ponds. Detention Ponds. CIVL 1112 Detention Ponds - Part 1 1/12

WASTEWATER TREATMENT OBJECTIVES

User s Manual for the BMPTRAINS Model

managing stormwater stormwater PARTNERS An introduction to maintaining stormwater facilities ~ for private property owners and HOAs SW WASHINGTON

Industrial Storm Water Best Management Practices. Restoring, maintaining, and enhancing the quality of Oregon's water.

Florida Department of Environmental Protection

TARP Section 2.2 Stormwater BMP Screening for Validation

Stormwater Quality Monitoring Report

Final Report of the Town Owned Lands Improvement Project for the Town of Brentwood, NH

Pollution Control NEW! NEW! Stormwater Attenuation Systems Sustainable Urban Drainage Solutions for Domestic & Commercial Applications. klargester.

BEST MANAGEMENT PRACTICES (BMPs)... What are They? GOOD HOUSEKEEPING PRACTICES Your Business Should Employ

Watershed Treatment Model for Urban Watersheds. Neely L. Law Watershed Analyst Center for Watershed Protection

GUIDELINE FOR MUNICIPAL MANAGEMENT PRACTICES FOR STREET SWEEPINGS & CATCH BASIN CLEANINGS

Applicability of Inlet Filters, Oil/Water Separators, Hydrodynamic Separators, and Media Filters

Chapter 2 Stormwater Pollution Prevention Plan (SWPPP) for Park Operations

Stormwater management around the world Lessons from Novatech 2010 Dennis Corbett and Marion Urrutiaguer

WATER EFFLUENT AND SOLID WASTE CHARACTERISTICS IN THE PROFESSIONAL CAR WASH INDUSTRY. A Report for the International Carwash Association

Soakage Trenches. A better way to manage stormwater. Thinking Globally and Acting Locally

Minimizes sediment and debris from entering storm drains that lead to waterways and watercourses.

Final Draft Prepublication Copy

APPENDIX F. RESIDENTIAL WATER QUALITY PLAN: ALLOWABLE BMP OPTIONS

CLACKAMAS COUNTY ZONING AND DEVELOPMENT ORDINANCE

ADVANCED TREATMENT SYSTEMS OVERVIEW State of Washington

Guidelines for. Permeable Pavement

URBAN STORMWATER GUIDELINES AND BEST MANAGEMENT PRACTICES FOR PROTECTION OF FISH AND FISH HABITAT DRAFT DISCUSSION DOCUMENT

Costs for Green Infrastructure and Stormwater Controls

Storm Drain Inlet Protection

Examining the Clogging Potential of Underdrain Material for Stormwater Biofilter

Maine Department of Environmental Protection Program Guidance On Combined Sewer Overflow Facility Plans

RULE ORGANIC COMPOUNDS - WASTEWATER COLLECTION AND SEPARATION SYSTEMS

Storm Drain Inlet Protection

A Developer s Guide: Watershed-Wise Development

Conveyance means a mechanism for transporting water from one point to another, including pipes, ditches, and channels.

Application for Controlled Trade Waste Discharge Approval

Burnsville Stormwater Retrofit Study

A SURVEY OF INSTALLATION AND MAINTENANCE COSTS OF STORMWATER TREATMENT FACILITIES. for

Permeable Interlocking Concrete Pavements

Post-Construction Stormwater Management Checklist* (5,000 SF or Greater)

BMP #: Dry Wells / French Drains

Technical Bulletin // Up-Flo Filter

Operations and Maintenance Plan The Residences at Johnson Farm 189 Landham Road Sudbury, Massachusetts. Submitted to: Town of Sudbury

8.1.3 General Design Guidelines. The following guidelines shall be used when designing inlets along a street section:

Land Disturbance, Erosion Control and Stormwater Management Checklist. Walworth County Land Conservation Department

Compost-Amended Vegetated Filter Strip Performance Monitoring Project

Costs for Green Infrastructure and Stormwater Retention Practices

Final Report THE COST AND EFFECTIVENESS OF STORMWATER MANAGEMENT PRACTICES

stormwater BMP Total Cost Analysis

STORMWATER MONITORING: POLLUTANTS, SOURCES, AND SOLUTIONS

City of East Lansing CSO Control Facility Evaluation Demonstrative Approach to Meet WQS

Peter J. Strazdas Associate Vice President, Facilities Management Western Michigan University

Permeable Pavers. calstone.com. Permeable Interlocking Concrete Pavements (PICP s)

Phosphorus. Phosphorus Lake Whatcom Cooperative Management.

Selection of Stormwater Treatment Facilities For Maximum Extent Practicable Treatment Effectiveness in Compliance with NPDES Provision C.

Evaluating Drain Inlet Cleaning as a Storm Water Best Management Practice

IC24. DISPOSAL OF WASTEWATER GENERATED BY MOBILE BUSINESSES AND OUTDOOR ACTIVITIES

Removing Dissolved Phosphorus from Stormwater

How To Amend A Stormwater Ordinance

Stormwater Operations & Maintenance Plan

Chapter 5.0. Stormwater Credits for Innovative Site Planning

City of Atlanta. Department of Watershed Management. Post-Development Stormwater Management Ordinance Summary of Revisions

GUIDELINES FOR SOIL FILTER MEDIA IN BIORETENTION SYSTEMS (Version 2.01) March 2008

Toronto s Wet Weather Flow Master Plan

Compost-Based Stormwater Best Management Practices Using Compost to Improve Stormwater Management and Erosion Control On Roadsides

Engineering Specifications February, 2004 Schedule H to Bylaw 7452, Subdivision Bylaw Page 18

A San Antonio Case Study on the Water Quantity and Quality Benefits of LID Development

NPDES Permit No. IL Notice No bwc. Public Notice Beginning Date: June 6, Public Notice Ending Date: July 8, 2013

MEMBRANE TECHNOLOGY TREATING OILY WASTEWATER FOR REUSE

Watershed-Wide Modeling for TMDL/MS4 Permit Compliance. Greg Wilson, Barr Engineering

1.3 Wastewater and Ambient Water Quality

Maintaining water sensitive urban design elements

MBJ Environmental Programmes

Stormwater Best Management Practices (BMP) Performance Analysis

WASHINGTON STATE DEPARTMENT OF TRANSPORTATION SUMMARY OF INVENTORY FINDINGS:

First in Service First in Safety

Permeable Pavement Operation & Maintanence Guide

NPDES Industrial Stormwater Inspection Worksheet

Transcription:

Chapter 2 Treatment Facility Menus This chapter identifies the treatment facility menus. The menus in this chapter are as follows: Oil Control Menu, Section 2.1 Phosphorus Treatment Menu, Section 2.2 Enhanced Treatment Menu, Section 2.3 Basic Treatment Menu, Section 2.4 Performance goals apply to the water quality design storm volume or flowrate, whichever is applicable, and apply on an average annual basis to the entire annual discharge volume (treated plus bypassed). The incremental portion of runoff in excess of water quality design flowrate can be routed around the facility (offline treatment facilities) or can be passed through the facility untreated (online treatment facilities) provided a net pollutant reduction is maintained. All performance goals apply to stormwater typically found in Pacific Northwest maritime climates, where long duration, low intensity storms predominate and stormwater contains mostly silt-sized particles. 2.1 Oil Control Menu This menu is applicable in addition to facilities required by other treatment menus. 2.1.1 Performance Goal The oil control menu facility options should achieve the goals of no ongoing or recurring visible sheen, and to have a 24-hour average Total Petroleum Hydrocarbon (TPH) concentration no greater than 10 mg/l, and a maximum of 15 mg/l for a discrete sample (grab sample). 2.1.2 Options Oil control options include facilities that are small, treat runoff from a limited area, and require frequent maintenance as well as facilities that treat runoff from larger areas and generally require less frequent maintenance. API-Type Oil/Water Separator See Chapter 11 Coalescing Plate Oil/Water Separator See Chapter 11 Linear Sand Filter See Chapter 8 The linear sand filter is used in the Basic, Enhanced, and Phosphorus Treatment menus also. If used to satisfy one of those treatment requirements, the same facility shall not also be used to satisfy the oil control requirement unless enhanced maintenance is assured. This is to prevent clogging of the filter by oil so that it will function for suspended solids and other pollutant removal as well. Quarterly cleaning is required when used as a combination facility. Emerging Stormwater Treatment Technologies for Oil Treatment See Chapter 12 Chapter 2 5-5 Volume 5

City of Tacoma 2.1.3 Application on the Project Site Place oil control facilities upstream of other facilities, as close to the source of oil generation as practical. For high-use sites located within a larger commercial center, only the impervious surface associated with the high-use portion of the site is subject to oil treatment requirements. If common parking for multiple businesses is provided, treatment shall be applied to the number of parking stalls required for the high-use business only. If the treatment collection area also receives runoff from other areas, the treatment facility must be sized to treat all water passing through it. High-use roadway intersections shall treat lanes where vehicles accumulate during the traffic signal cycle, including left and right turn lanes and through lanes, from the beginning of the left turn pocket. If no left turn pocket exists, the treatable area shall begin at a distance equal to three car lengths from the stop line. If runoff from the intersection drains to more than two collection areas that do not combine within the intersection, treatment may be limited to any two of the collection areas. 2.2 Phosphorus Treatment Menu 2.2.1 Performance Goal The phosphorus menu facility choices should achieve a goal of 50% total phosphorus removal for a range of influent concentrations between 0.1 0.5 mg/l. The phosphorus menu facility choices must achieve basic treatment goals in addition to phosphorus. 2.2.2 Options Any one of the following options may be chosen to satisfy the phosphorus treatment requirement. Infiltration with appropriate pretreatment See Chapter 7. Infiltration Treatment - If infiltration is through soils meeting the minimum site suitability criteria for infiltration treatment (see Chapter 7), a presettling basin or a basic treatment facility can serve for pretreatment. Infiltration Preceded by Basic Treatment - If infiltration is through soils that do not meet the soil suitability criteria for infiltration treatment, treatment must be provided by a basic treatment facility unless the soil and site fit the description in the next option below. Infiltration Preceded by Phosphorus Treatment - If the soils do not meet the soil suitability criteria and the infiltration site is within ¼ mile of a phosphorus-sensitive receiving water, or a tributary to that water, treatment must be provided by one of the other treatment facility options listed below. Large Sand Filter See Chapter 8 Large Wetpond See Chapter 10 Emerging Stormwater Treatment Technologies for Phosphorus Treatment See Chapter 12 Two-Facility Treatment Trains See Table 5-1 Volume 5 5-6 Chapter 2

Table 5-1: Treatment Trains for Phosphorus Removal First Basic Treatment Facility Biofiltration Swale Second Treatment Facility Linear Sand Filter (no presettling needed) Linear Sand Filter Basic Wetpond Wetvault Stormwater Treatment Wetland Basic Combined Detention and Wetpool 2.3 Enhanced Treatment Menu 2.3.1 Performance Goal The enhanced treatment facility choices should provide a higher rate of removal of dissolved metals than basic treatment facilities. The performance goal assumes that the facility is treating stormwater with influent dissolved copper ranging from 0.003 to 0.02 mg/l, and dissolved zinc ranging from 0.02 to 0.3 mg/l. Enhanced treatment facilities must achieve basic treatment goals in addition to enhanced treatment goals. 2.3.2 Options Any one of the following options may be chosen to satisfy the enhanced treatment requirement: Infiltration with appropriate pretreatment See Chapter 7 Infiltration Treatment - If infiltration is through soils meeting the minimum site suitability criteria for infiltration treatment (see Chapter 7, a presettling basin or a basic treatment facility can serve for pretreatment. Infiltration Preceded by Basic Treatment - If infiltration is through soils that do not meet the soil suitability criteria for infiltration treatment, treatment must be provided by a basic treatment facility unless the soil and site fit the description in the next option below. Infiltration Preceded by Enhanced Treatment - If the soils do not meet the soil suitability criteria and the infiltration site is within ¼ mile of a fish-bearing stream, a tributary to a fish-bearing stream, or a lake, treatment must be provided by one of the other treatment facility options listed below. Large Sand Filter See Chapter 8 Stormwater Treatment Wetland See Chapter 10 Two Facility Treatment Trains See Table 5-2 Compost-Amended Filter See Chapter 9 Bioretention/rain garden See Volume 6 Chapter 2 5-7 Volume 5

City of Tacoma Emerging Stormwater Treatment Technologies for Enhanced Treatment See Chapter 12 Table 5-2: Treatment Trains for Enhanced Treatment First Basic Treatment Facility Biofiltration Swale Linear Sand Filter Basic Wetpond Wetvault Basic Combined Detention/Wetpool with a presettling cell if the filter isn t preceded by a detention facility Second Treatment Facility Media Filter a Linear Sand Filter with no presettling cell needed a. The media must be of a type approved for use by Ecology. Refer to Ecology s website. 2.4 Basic Treatment Menu 2.4.1 Performance Goal The basic treatment menu facility options should achieve 80% removal of total suspended solids (TSS) for influent concentrations ranging from 100 to 200 mg/l. For influent concentrations greater than 200 mg/l, a higher treatment goal is appropriate. For influent concentrations less than 100 mg/l, the facilities should achieve an effluent goal of 20 mg/l total suspended solids. 2.4.2 Options Any one of the following options may be chosen to satisfy the basic treatment requirement: Infiltration See Chapter 7 Sand Filters See Chapter 8 Biofiltration Swales See Chapter 9 s See Chapter 9 Basic Wetpond See Chapter 10 Volume 5 5-8 Chapter 2

Wetvault See Chapter 10 A wetvault may be used for commercial, industrial, or road projects if there are space limitations. The use of wetvaults is discouraged for residential projects. Combined detention/wetvaults are allowed. Stormwater Treatment Wetland See Chapter 10 Combined Detention and Wetpool Facilities See Chapter 10 Bioretention/Rain Garden See Volume 6 Emerging Stormwater Treatment Technologies for Basic Treatment See Chapter 12 Chapter 2 5-9 Volume 5