State of Technology for Rehabilitation of Wastewater Collection Systems
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Infiltration/Inflow Task Force Report
INFILTRATION/INFLOW TASK FORCE REPORT A GUIDANCE DOCUMENT FOR MWRA MEMBER SEWER COMMUNITIES AND REGIONAL STAKEHOLDERS MARCH 2001 INFILTRATION/INFLOW TASK FORCE REPORT A GUIDANCE DOCUMENT FOR MWRA MEMBER SEWER COMMUNITIES AND REGIONAL STAKEHOLDERS MARCH 2001 Executive Summary This report is the product of the Infiltration/Inflow (I/I) Task Force. It has been developed through the cooperative efforts of the 43 Massachusetts Water Resources Authority (MWRA) member sewer communities, MWRA Advisory Board, The Wastewater Advisory Committee (WAC) to the MWRA, Charles River Watershed Association (CRWA), Fore River Watershed Association (FRWA), Mystic River Watershed Association (MRWA), Neponset River Watershed Association (NRWA), South Shore Chamber of Commerce (SSCC), Massachusetts Department of Environmental Protection (DEP), United States Environmental Protection Agency (EPA), and MWRA. The I/I Task Force recommends implementation of the regional I/I reduction goals and implementation strategies detailed in this report. The report outlines a regional I/I reduction plan with appropriate burdens and benefits for stakeholders. The report is intended to be a guidance document for use by local sewer communities, as well as other regional stakeholders, who may tailor appropriate aspects of the report recommendations to their unique situations. Severe storms in October 1996 and June 1998 led to the unusual circumstance of numerous sanitary sewer overflows (SSOs) from local and MWRA collection systems. In the aftermath of these events, EPA and DEP began an aggressive effort to make MWRA regulate flows from community sewer systems. MWRA recommended cooperative efforts by local collection system operators, as well as regulators and environmental advocates, would be more effective than a prescriptive, enforcement based approach. -
Ssos and Csos What Are They and What Are We Doing About Them?
SSOs and CSOs What are they and what are we doing about them? Don Kennedy – Training Coordinator James LaLiberte – Training Coordinator Combined sewers were introduced to the larger American cities in the mid-19th century. They were designed to dry out streets by collecting rainwater runoff, domestic sewage from newly invented flush toilets, and industrial wastewaters all in the same pipe. In dry weather, a combined sewer system sends a town’s entire volume of wastewater to a treatment plant, which treats and discharges to a waterway. The problems, generally, arise during heavy or extended rain events which can overload the system and seek relief. Such events can result in either a Sanitary Sewer Overflow (SSO), a Combined Sewer Overflow (CSO), or both. While both situations act as a relief for the system, one is intentional and the other is not. An SSO is an unintentional discharge of wastewater to the environment or personal property. SSOs are, generally, the result of poor sewer management and maintenance. Flow through sewer lines can be restricted by fats, oils and greases (FOG) or by tree roots. The system then does not have the capacity to handle a significant rain event, resulting in wastewater escaping through manholes, residences or businesses. TREE ROOTS IN SEWER Other contributors to the system are Inflow and Infiltration. These situations allow stormwater to enter the sewer system which shouldn’t. Infiltration - through bad joint or cracked pipes. Inflow – through illegal or unapproved connections, such as roof gutters, yard -
Inflow and Infiltration Reduction in Sanitary Sewers
Appendix E-4 – Inflow and Infiltration Reduction in Sanitary Sewers INFLOW AND INFILTRATION REDUCTION IN SANITARY SEWERS D.1 Introduction to RDII in Sanitary Sewers A properly designed, operated and maintained sanitary sewer system is meant to collect and convey all of the sewage that flows into it to a wastewater treatment plant. Rainfall dependent infiltration and inflow (RDII) into sanitary sewer systems has long been recognized as a major source of operating problems that cause poor performance of many sewer systems including system overflows. The extent of infiltration also correlates with the condition of aging sewers. The three major components of wet-weather wastewater flow into a sanitary system – base wastewater flow (BWWF), groundwater infiltration (GWI), and RDII are illustrated in Figure D-1 and are discussed below. Figure D-1: Three components of wet-weather wastewater flow BWWF, often called base sanitary flow, is the residential, commercial, institutional, and industrial flow discharged to a sanitary sewer system for collection and treatment. BWWF normally varies with water use patterns within a service area throughout a 24-hour period with higher flows during the morning period and lower during the night. In most cases, the average daily BWWF is more or less constant during a given day, but varies monthly and seasonally. BWWF often represents a significant portion of the flows treated at wastewater treatment facilities. GWI represents the infiltration of groundwater that enters the collection system through leaking pipes, pipe joints, and manhole walls. GWI varies throughout the year, often trending higher in late winter and spring as groundwater levels and soil moisture levels rise, and subsiding in late summer or after an extended dry period. -
Decentralized Systems Technology Fact Sheet: Septic Tank Systems for Large Flow Application
United States Office of Water EPA 832-F-00-079 Environmental Protection Washington, D.C. September 2000 Agency Decentralized Systems Technology Fact Sheet Septic Tank Systems for Large Flow Applications DESCRIPTION Three main types of septic tanks are used for wastewater treatment: A septic tank system is a traditional wastewater treatment technology utilizing treatment in a tank • Concrete. system followed by soil absorption. The system operates on gravity and has been used in residential • Fiberglass. areas for decades. A modification to the traditional system is an enlargement to accommodate many • Polyethylene/plastic. homes and/or commercial discharges. This is accomplished with individual septic tanks followed All tanks must be watertight because groundwater by a community collection and subsurface disposal entering the system can saturate the soil absorption system, or a community collection system followed field, resulting in a failed system. Furthermore, in by a single treatment system. Commercial instances where septic tanks precede a secondary establishments, such as restaurants, nursing homes, treatment process, excess groundwater may hospitals and other public use areas do not generally inundate the downstream process, causing it to use septic tank systems due to oil & grease, odor, perform poorly. and flow issues. From the septic tank, the clarified wastewater The primary device in treatment is a septic tank passes through the tank outlet and enters the soil enclosed in a watertight container that collects and absorption field. The most common outlet is a tee provides primary treatment of wastewater by fitting connected to the pipe leading to the soil separating solids from the wastewater. The tank absorption field. -
Grease Basins Approved For
Lake County Department of Public Works List of Approved Grease Removal Systems and Sampling Stations The following lists Manufacturers of Grease Removal Systems and Sampling Stations. This list is provided as a service to the food service establishments by the Lake County Public Works Department and does not constitute an endorsement of any company listed on the following pages. The Lake County Public Works Department will accept grease removal units, other than those specified in this document, providing that the grease removal unit satisfies all criteria outlined in the County Sewer Use Ordinance and the Variance Procedure is properly followed. The following is a list of Passive Interior Device (PID) and Passive Exterior Device (PED) manufacturers and the acceptable model numbers. These devices recover and remove oils and grease from the effluent waste stream. The oils and grease recovered are manually pumped and can be recycled or disposed of in solid waste. Zurn Green Turtle Acceptable Models Proceptor® 2709 Water Ridge Parkway Suite 410 All GMC Models between Charlotte, NC 28217 GMC500- GMC1500 (704) 295-1733 *GMC250 (Min Interior) www.greenturtletech.com Schier Products Acceptable Models 9500 Woodend Road Great Basin Models Edwardsville, KS 66111 GB500 – GB1000 (913) 951-3399 Big Foot Models www.schierproducts.com GGI750- GGI1500 *GB250 (Min Interior) * Requires a variance for interior applications. The following is a list of Sampling Station manufacturers and the acceptable model numbers. Schier Products Acceptable Models 9500 Woodend Road Exterior: SV24-L4, SV24-L6, Edwardsville, KS 66111 SV24-O4, SV24-O6 (913) 951-3399 Interior: SV4-L4, SV4-L6, www.schierproducts.com SV4-O4 Automatic Recovery Devices Acceptable Models Thermaco Big Dipper PO Box 2548 Contact mfg. -
Inflow & Infiltration
Inflow & Public Education Infiltration Committee This municipal water quality educational material was sponsored by the Public Municipal Water Quality Education Committee of the Public Educational Information Pennsylvania Water Environment Association (PWEA). PWEA is a Member Association of the Water Environment Federation (WEF). Please visit our Public Education Toolbox on PWEA’s website for other public educational material for the municipal water quality industry. PO Box 3367 Gettysburg, PA 17325 www.pwea.org www.pwea.org Inflow & Infiltration “I&I” is a short acronym for a huge problem most sewer communities face, Inflow and Infiltration. Inflow occurs when rainwater is misdirected into the sanitary sewer system instead of storm sewers. Examples are: roof leaders, footer drains, sump pumps, manhole covers, and cross connections from storm drains. The remedy for inflow is to remove improper connections to the sanitary sewer system. Infiltration occurs when ground water seeps into the sanitary The worst impact of I&I is the likelihood You, as a homeowner, can reduce I&I sewer system through cracks or that the sewage can overflow out of the from your property. leaks in sewer pipes. The cracks sewer pipe and into our environment. This • Check that gutters and outside drains or leaks may be caused by age yucky, gross runoff of untreated sewage, are not connected to sanitary sewers. related deterioration, loose joints, contaminated with fecal matter, urine, and • Avoid planting trees and shrubs over damage or root infiltration. The toilet paper, is often referred to as SSO building sewers. The roots can remedy for infiltration is repairing (Sanitary Sewer Overflow). -
Sanitary Sewer Overflow Response Plan
CITY OF HEMET WASTEWATER DIVISION SANITARY SEWER OVERFLOW RESPONSE PLAN Appendix D of the City of Hemet Sewer System Management Plan Updated February 2016 City of Hemet Wastewater Department SANITARY SEWER OVERFLOW RESPONSE PLAN Table of Contents CHAPTER 1 INTRODUCTION ........................................................................................... 4 1.1 Regulatory Requirements ................................................................................................. 4 1.1.1 Statewide General Waste Discharge Requirements (GWDR) .................................. 4 CHAPTER 2 SPILL CATEGORIES AND REQUIREMENTS ........................................ 5 2.1 Summary of MRP Requirements ..................................................................................... 5 2.1.1 Spill Category 1 Discharges...................................................................................... 5 2.1.2 Spill Category 2 Discharges...................................................................................... 6 2.1.3 Spill Category 3 Discharges...................................................................................... 6 2.1.4 No Spill Certification ................................................................................................ 7 2.1.5 Private Lateral Sewage Discharge ............................................................................ 7 CHAPTER 3 RESPONSE TO NOTIFICATION OF SPILL ............................................. 8 3.1 Public Report of SSOs..................................................................................................... -
In the United States District Court for the Western District of Missouri Western Division
IN THE UNITED STATES DISTRICT COURT FOR THE WESTERN DISTRICT OF MISSOURI WESTERN DIVISION UNITED STATES OF AMERICA, ) ) ) ) ) ) Civil Action No. 4:10-cv-0497-GAF Plaintiff, ) ) v. ) ) THE CITY OF KANSAS CITY, ) MISSOURI ) ) Defendant. ) ) THE STATE OF MISSOURI ) ) Non-aligned Party, ) Joined pursuant to 33 U.S.C. § 1319(e) ) ) ) ) THIRD AMENDED CONSENT DECREE Case 4:10-cv-00497-GAF Document 22 Filed 01/15/21 Page 4 of 107 TABLE OF CONTENTS I. JURISDICTION ........................................................................................................... 6 II. VENUE .......................................................................................................................... 6 III. BINDING EFFECT ...................................................................................................... 6 IV. PURPOSE ..................................................................................................................... 7 V. DEFINITIONS .............................................................................................................. 8 VI. SUBMISSIONS REQUIRING EPA AND STATE APPROVAL .......................... 16 VII. IMPLEMENTATION OF SEWER SYSTEM REMEDIAL MEASURES AND POST-CONSTRUCTION MONITORING ............................................................. 19 VIII. FUNDING ................................................................................................................... 29 IX. REPORTING ............................................................................................................. -
Fats, Oils and Grease (Fog)
CITY OF TULSA FATS, OILS AND GREASE (FOG) One of the worst things that can happen to a home or business is discovering a sewage overflow due to plumbing problems. More often than not, when those overflows are investigated the cause is clear — fats, oils and grease (FOG) have clogged the pipes and prevented it from performing its duty. According to the Environmental Protection Agency, 47 percent of sanitary sewage overflows (SSOs) are caused by FOG. This is unsurprising when you learn that a single restaurant can contribute anywhere from 800 to 17,000 pounds of grease per year to our wastewater treatment plants. How Does FOG Cause Problems? Think of the pipes in our sewer system as the veins leading to the beating heart of the city — our wastewater treatment plant. When FOG is sent down the drain, particles separate from the water and cling to the walls of the pipes. As this continues, buildup occurs until a pipe is so clogged that it may be reduced to a fraction of its normal capacity. This reduction in size can lead to backflow and sewage overflow on your property or your downstream neighbor's property. If one of those areas of buildup hardens like plaque, it has the potential to break off and then cause a “heart attack” as it reaches the center of the system. Proper FOG disposal can prevent this kind of buildup and disruption to Tulsa’s wastewater system. Preventing FOG Buildup in Businesses For food-handling organizations, taking precautions to avoid sending Clean up spills immediately with disposable wipes or an FOG into the sewer system not only saves the city time and money but absorbent (e.g. -
Sanitary Sewer Overflow Report Side a Category 1: Discharge of Untreated Or Partially Treated Wastewater of Any Volume Resulting
Sanitary Sewer Overflow Report Side A Category 1: Discharge of untreated or partially treated wastewater of any volume resulting from a sanitary sewer system failure of flow condition that either (1) reaches surface water and/or drainage channel tributary to a surface water; OR (2) Reached a Municipal Separate Storm Sewer System (MS$) and was not fully captured and returned to the sanitary sewer system or otherwise captured and disposed of properly. Category 2: Discharge of untreated or partially treated wastewater greater than or equal to 1,000 gallons resulting from a sanitary sewer system failure or flow condition that either (1) Does not reach surface water, a drainage channel, or an MS4, OR (2) The entire SSO discharged to the storm drain system was fully recovered and disposed of properly. Category 3: All other discharges of untreated or partially treated wastewater resulting from a sanitary sewer system failure or flow condition. Spill from Private Lateral Describe in detail the basis for choosing the spill category: IMMEDIATE NOTIFICATION: If this is a Category 1 spill greater than or equal to 1,000 gallons, contact CalEMA within 2 hours at (800) 852-7550. A. SPILL LOCATION Spill Location Name: Latitude Coordinates*: Longitude Coordinates: Street Name and Number: Nearest Cross Street: City: Rancho Palos Verdes Zip: 90275 County: Los Angeles Spill Location Description: B. SPILL DESCRIPTION Spill Appearance Point (check one or more): Building/Structure Force Main Gravity Sewer Pump Station Other Structure (i.e. cleanout) Manhole-Structure ID# Other (specify): Did the spill reach a drainage channel and/or surface water: Yes (Category 1) No If the spill reached a storm sewer, was it fully captured and returned to the Sanitary Sewer? Yes No (Cat. -
Sewer Odor Control Master Plan
CITY OF LOS ANGELES SEWER ODOR CONTROL MASTER PLAN Wastewater Engineering Services Division Bureau of Sanitation AUGUST 2011 2011 Odor Control Master Plan TABLE OF CONTENTS Chapter Title Page ACRONYMS AND ABBREVIATIONS......................................................................... 3 EXECUTIVE SUMMARY .............................................................................................. 5 INTRODUCTION ..................................................................................................................................... 5 EVALUATION OF THE COLLECTION SYSTEM................................................................................. 6 RECOMMENDATIONS/CONSIDERATIONS ....................................................................................... 7 1.0 INTRODUCTION................................................................................................. 9 1.1 HISTORY OF THE SEWER SYSTEM................................................................................................. 9 1.2 ODOR GENERATION ..................................................................................................................... 9 1.3 HISTORY OF ODOR CONTROL..................................................................................................... 10 1.4 COLLECTION SYSTEM SETTLEMENT AGREEMENT AND ORIGIN OF THE MASTER PLAN .............. 13 1.5 PURPOSE AND OBJECTIVES......................................................................................................... 13 1.6 TASK DESCRIPTIONS -
Fats, Oil and Grease (FOG) Policies and Procedures Manual
Fats, Oil and Grease (FOG) Policies and Procedures Manual February 2018 Colorado Springs Utilities Industrial Pretreatment Program 701 East Las Vegas Street Colorado Springs, CO 80903 (719) 448-4800 . Table of Contents EXECUTIVE SUMMARY. ......................................................................................................................................... 1 . INTRODUCTION ................................. ........................................................................................................................ 1 DEFINITIONS ................................. .............................................................................................................................. 2 LEGAL AUTHORITY ................................ ................................................................................................................ 4 PRETREATMENT PROGRAM AUTHORITY .................................................................................................................... 4 FOG CONTROL AUTHORITY ....................................................................................................................................... 4 BMP REQUIREMENTS ............................................................................................................................................. 6 DESCRIPTION AND APPLICABILITY ............................................................................................................................. 6 FOOD SERVICE ESTABLISHMENTS .............................................................................................................................