Approaches to Addressing Bacteria Impairments Kevin Wagner Texas Water Resources Institute.

Slides:



Advertisements
Similar presentations
1 Watershed Planning: A Key to Integrated Planning FHWA Environmental Conference Ann Campbell Wetlands Division.
Advertisements

ALLEN BERTHOLD TEXAS WATER RESOURCES INSTITUTE Water Quality and Copano Bay Watershed Efforts.
What are TMDLs? and What Might They Mean to MS4 Permittees?
Watershed Planning for the South and North Llano Rivers Aaron Wendt Texas State Soil and Water Conservation Board Public Stakeholder Meeting August 14,
Water Quality Trading Claire Schary Water Quality Trading Coordinator U.S. Environmental Protection Agency, Region 10, Seattle, WA Region 10, Seattle,
Prioritization Workgroup Summary. Workgroup Topics Nutrient results What is a watershed? What is a TMDL? Prioritization methods Basin framework and management.
Bureau of Water Overview Wastewater issues Drinking water issues Wrap up topics.
Nebraska Department of Environmental Quality TMDLs 101 An Explanation of the Federal Clean Water Act’s TMDL Requirements and How they Impact Carter Lake.
Nelly Smith EPA Region 6. - Develop or revise bacteria reduction program for consistency with new TMDL requirements and allocations - Develop or revise.
Nutrient Trading Framework in the Coosa Basin Alabama Water Resources Conference September 6, 2012 A Feasibility Study of Nutrient Trading in Support of.
Slide 1 EPA Stormwater & Water Regulations: Local Impacts & Balancing Power 2011 Congressional City Conference.
Clean Water Act Integrated Planning Framework Sewer Smart Summit October 23, 2012.
Overview of TMDL Plans TMDL Plan Workshop April 24, 2015 Karl Berger, COG staff Outline: Details Schedule Plan Elements Issues 1.
Bureau of Water Program Overview Local Government Interest.
IDEM TMDL 101 Everything you wanted to know about Total Maximum Daily Loads.
Current Planning for 2017 Mid-Point Assessment Gary Shenk COG 10/4/2012 presentation credit to Katherine Antos and the WQGIT ad hoc planning team.
Montana’s 2007 Nonpoint Source Management Plan Robert Ray MT Dept Environmental Quality.
Chesapeake Bay Restoration An EPA Perspective Jeff Corbin Senior Advisor to the Administrator U.S. EPA.
Incorporating the 9-Elements into a WMP Lindsey PhillipsMike Archer Source Water CoordinatorState Lakes Coordinator (402) (402)
Components of every Good Watershed Management Plan NDEQ – Planning Unit August 6 th, 2014 NDEQ – Planning Unit gust 6 th 2014.
EPA Region 6 Dallas, Texas EPA Region 6 Dallas, Texas.
9.Monitoring Plan + 10.Implementation Plan + 4. LAs* 5. WLAs* 6. MOS* 7.Seasonal Variation* 8.Reasonable Assurance + TMDL Process 1 Problem Understanding.
April 22, 2005Chester Creek Watershed TMDL Total Maximum Daily Load Chester Creek University Lake & Westchester Lagoon Alaska Department of Environmental.
Incorporating Climate Change Adaptation in EPA Region 10 Programs: An example based on a newly initiated pilot in the Office of Water and Watershed’s Total.
Lecture ERS 482/682 (Fall 2002) TMDL Assessment ERS 482/682 Small Watershed Hydrology.
Watershed Management Framework Mission of watershed management –Coordinate and integrate the programs, tools, and resources of multiple stakeholder groups.
Allen Berthold Texas Water Resources Institute. Review: Clean Water Act Goal of CWA is to restore and maintain water quality suitable for the “protection.
Minnesota Pollution Control Agency Setting the Course for Improved Water Quality A TMDL Training Program for Local Government Leaders and Other Water Resource.
Impaired and TMDL Waterbody Listings Impacts on DoD Facilities Bill Melville, Regional TMDL Coordinator
Lake Erie HABs Workshop Bill Fischbein Supervising Attorney Water Programs March 16, 2012 – Toledo March 30, Columbus.
Region 1 & 2 IR Workshop October 28,  The Water Quality Framework is a new way of thinking about how EPA’s data and information systems can be.
Total Maximum Daily Loads in MS4 Storm Water Programs.
1 ATTAINS: A Gateway to State-Reported Water Quality Information Webcast Sponsored by EPA’s Watershed Academy June 18, 2008, 11:30am-1:30pm EST Shera Bender,
VIRGINIA’S TMDL PROCESS.
Federal Clean Water Act Monitoring and assessments completed statewide Standards not met? Section 303 (d) requires placing the water body on the “Impaired.
1 Sandra Spence EPA Region 8 TMDL Program EPA Region 8 TMDL Program Integrating Watershed Plans and TMDLs to Help Answer Watershed Planning Questions November.
Sustaining Long Term Regional Coordinated Monitoring Programs Todd Running, H-GAC May 9, 2006.
Teresa Marks Director 1. o The Clean Water Act of 1972 requires states to establish water quality standards (WQS) for all waterbodies within the state.
Phase II WIP Background & Development Process Tri-County Council – Eastern Shore June 2,
Presentation to the Chesapeake Bay and Water Resources Policy Committee July 30, 2010.
Restoring VA Waters the TMDL Way Jeff Corbin Senior Advisor to the Regional Administrator U.S. EPA Region 3.
Straight to the Point – Watershed-based Plans Should: be designed to restore water quality from nonpoint source impairments using sufficiently analyzed.
EPA Chesapeake Bay Trading and Offsets Workplan June 1, 2012.
Eric Agnew Environmental Regulations February 15, 2006.
Wisconsin’s Nutrient Reduction Strategy for Water Quality Wisconsin Crop Management Conference January 16, 2014 Ken Genskow, PhD Associate Professor, Department.
West Metro Water Alliance A Path to Clean Water – Understanding TMDLs and Watershed Planning September 21, 2011 Diane Spector Wenck Associates, Inc.
Fecal Bacteria Total Maximum Daily Loads (TMDL) in 4 Austin Watersheds Presented to the City of Austin Environmental Board November 7, 2012.
Overview of the Total Maximum Daily Load Program.
76. The central U.S. law regulating water quality is the Clean Water Act (CWA), adopted in The Act initially focused on point sources, which it.
Stream Health Outcome Biennial Workplan Neely L. Law, PhD Center for Watershed Protection Chesapeake Bay Program Sediment & Stream Coordinator Habitat.
REVISIONS TO THE FEDERAL WATER QUALITY STANDARDS RULE JILL CSEKITZ, TECHNICAL SPECIALIST TEXAS COMMISSION ON ENVIRONMENTAL QUALITY.
CITIZENS ADVISORY COMMITTEE SPRING MEETING MARCH 1—2, 2012 CHARLOTTESVILLE, VA EPA’s Evaluation of Bay Jurisdictions’ Draft Phase II WIPs & Final
Commonwealth of Virginia TMDL Program Update Citizen for Water Quality Annual Summit September 22, 2001.
Modeling Fecal Bacteria Fate and Transport to Address Pathogen Impairments in the United States Brian Benham Extension Specialist and Associate Professor,
1975 EPA Study  Extensive construction in 1950s -1970s  Poor canal flushing results in “stagnation, putrification, and excessive nutrient enrichment.
Nutrients and the Next Generation of Conservation Presented by: Tom Porta, P.E. Deputy Administrator Nevada Division of Environmental Protection President,
Commonwealth of Virginia Fecal Coliform Bacteria TMDLs Four Mile Run Public Meeting #1 June 14, 2001.
CHRIS ZADAK AND RACHEL OLMANSON, METR0-ST. CROIX WATERSHED UNIT WATERSHED RESTORATION AND PROTECTION STRATEGY.
Ashley Wendt Texas State Soil & Water Conservation Board NPS Project Manager.
Integrated Watershed Management
VIRGINIA’S TMDL PROCESS Four Mile Run Bacteria TMDL March 25, 2002
Total Maximum Daily Load Program
Tim Cawthon TCEQ Nonpoint Source Program
The Total Maximum Daily Load (TMDL) Program in Illinois
Mike Bira EPA Region 6 NPS Program
Lake Erie HABs Workshop
Straight to the Point – Watershed-based Plans Should:
High Rock Lake TMDL Development
The Nine Elements that Must Be Included in a 319 Watershed Based Plan
Upper Clark Fork Watershed Restoration and TMDLs
Presentation transcript:

Approaches to Addressing Bacteria Impairments Kevin Wagner Texas Water Resources Institute

Watershed Action Planning “A process for coordinating, documenting, and tracking strategies and activities to protect and improve water quality.” ▫Simplify coordination regarding water quality planning activities ▫Seeks greater local participation from stakeholders ▫Process to determine which approach is best given available data and stakeholder input

Alternatives to Addressing Bacteria Impairments Water Quality Standards Review ▫Use Attainability Analysis (UAA) and Recreational Use Attainability Analysis (RUAA) Planning ▫Total Maximum Daily Loads  And Implementation Plan ▫Watershed Protection Plan

Water Quality Standards Review UAAs are assessments of the physical, chemical, biological, and economic factors affecting attainment of a waterbody use. UAAs are used to identify and assign attainable uses and criteria to individual waterbodies. Applicable uses and associated criteria are defined in the Texas Surface Water Quality Standards So, UAAs are used to set the most appropriate water quality standard for each particular waterbody taking into account it’s unique characteristics Slide borrowed from Water Monitoring Solutions

Bacteria Criteria Water quality standards create a tiered set of criteria for the 4 categories ▫PCR = 126 ▫SCR1 = 630 ▫SCR2 = 1,030 ▫NCR = 2,060 To put these proposed water quality standards in place, a RUAA must be performed to determine what level of recreation is actually occurring Slide borrowed from Water Monitoring Solutions

Recreational Use Attainability Analysis Sampling Conditions: Conducted during normal warm season (March-October) during baseflow conditions. Site Reconnaissance and Selection: Locate areas where the waterbody is accessible to the public and have highest potential for recreational use. Describe hydrologic characteristics, such as stream type, stream flow, hydrologic alterations, etc. Choose 3 sites per every 5 miles of stream. Slide borrowed from Water Monitoring Solutions

Recreational Use Attainability Analysis Stream Surveys: Measure the width, depth, and flow of stream to assess if recreation can physically take place Photographic Record: A photographic record must be made of each site during the site survey. Photographs should include an upstream view, left and right bank views, downstream view, any evidence of observed uses or indications of human use, hydrologic modifications, etc. Assess the condition of the riparian area and ease of bank access to the stream Slide borrowed from Water Monitoring Solutions

Recreational Use Attainability Analysis Historical Information: A historical review of recreational uses of the water body back to November 28, 1975 should be conducted. Interviews: Interviews from users present during the field survey, streamside landowners and local residents should be conducted in order to obtain information on existing and historical uses Slide borrowed from Water Monitoring Solutions

Total Maximum Daily Loads (TMDLs)

A budget for pollution in the stream Defines the maximum amount (or load) of a pollutant that a waterbody can assimilate on a daily basis and still meet water quality standards Allocates pollutant loads between point and non- point sources Requires adoption by TCEQ and must be approved by USEPA Slide borrowed from TSSWCB

TMDL Allocations TMDL = WLA + LA + MOS ▫WLA = Waste load Allocation = regulated sources ▫LA = Load Allocation = Non-regulated sources ▫MOS = Margin of Safety Implementation Plan ▫Developed by local stakeholders ▫Typically a 3-5 year plan of activities ▫Revised periodically to evaluate the process of improving water quality and revised as necessary Slide borrowed from TCEQ

TMDL: Wastewater Treatment Facilities Permit limits for E. coli concentration Monitoring requirements for E. coli Facilities in TMDL watersheds will receive E. coli concentration limits Other stakeholder initiated requirements may be in Implementation plan. Slide borrowed from TCEQ

TMDL: Urban and Suburban Storm Water (TPDES MS4 Permits) TPDES Storm water permits must be consistent with TMDL and Implementation Plan USEPA does not require numeric limits in MS4 permits Storm water quality improvement strategies will be identified in the Implementation Plan Strategies will be set by stakeholders Slide borrowed from TCEQ

TMDL: Non-Regulated Sources Involved in Implementation process Requirements will be set by stakeholders

TMDL Implementation Plans Based on environmental target of TMDL, the I- Plan is developed Prescribes measures necessary to mitigate human-caused sources of that pollutant in that waterbody Specifies limits for point source dischargers & recommends best management practices for nonpoint sources Can be revised by stakeholders to incorporate adaptive management Only requires State approval

Watershed Protection Plans (WPPs) Slide borrowed from TSSWCB

Watershed Protection Plans: WPPs are mechanisms for voluntarily addressing complex water quality problems that cross multiple jurisdictions WPPs holistically address all of the sources and causes of impairments and threats to both surface and ground water resources within a watershed WPPs are coordinated frameworks for implementing prioritized and integrated protection and restoration strategies driven by environmental objectives Slide borrowed from TSSWCB

WPPs WPPs are tools to better leverage the resources of individual landowners and citizens, local governments, state and federal agencies, and non- governmental organizations WPPs are developed and implemented through diverse, well integrated partnerships with decision-making founded at the local level WPPs also use adaptive management to modify the plan based on stakeholder input Slide borrowed from TSSWCB

9 Key Elements of a WPP a) Identification of the causes and sources of water quality problems b)Estimate of the load reductions expected to be achieved c)Description of management measures that will need to be implemented d)Estimate of technical and financial assistance needed to implement the plan e)Information/education component that will be used to enhance public understanding of the plan f)Schedule for implementing management measures g)Interim, measurable milestones for determining whether management measures are being implemented h)Set of criteria used to determine whether load reductions are being achieved i)Water quality monitoring component to evaluate effectiveness of implementation Slide borrowed from TSSWCB

Merits of WPPs Holistic –protection & restoration Coordinated framework of strategies Partnerships Stakeholder driven = decision-making Leverage resources Voluntary approach Adaptive Management Slide borrowed from TSSWCB

Merits of TMDL and I-Plans Results in automatic removal from 303(d) list TMDL approved by State & EPA ▫I-Plan only approved by State I-Plan developed in cooperation with regional and local stakeholders (further builds partnerships) Voluntary for non-point sources Leverage resources Adaptive management

WPP and TMDLs Side by Side Comparison of Watershed Protection Plans and Total Maximum Daily Loads Image from Google

Comparison of Watershed Plans and TMDL Components Watershed Plan Components 1.Build partnerships 2.Characterize the watershed Id waterbody, impairments, study boundaries Gather and analyze data Id causes and sources Estimate loads Slide borrowed from USEPA TMDL Components 1.Provide opportunity for public involvement 2.Identify the problem Id waterbody, impairments, study boundaries Gather and analyze data Id causes and sources (ie., WLA and LA) Estimate loads

Comparison of Watershed Plans and TMDL Components continued Watershed Plan Components 3.Sets goals and Id solutions Develop indicators/targets Determine load reductions Id critical areas Develop management measures to achieve goals Slide borrowed from USEPA TMDL Components 3.Identify water quality targets and goals and allocate loads Id critical areas and seasonality Describe technical analysis used in load estimation, load reduction, modeling, etc. Allocate acceptable loads between point and nonpoint sources (WLAs, LAs) Provide for a margin of safety (MOS)

Comparison of Watershed Plans and TMDL Components continued Watershed Plan Components 4.Design an implementation program Develop an implementation schedule Develop interim milestones Develop criteria to measure progress Develop monitoring component Develop educational component Id technical /financial assistance Assign responsibility TMDL I-Plan Components 4.Provide a monitoring and restoration strategy – Optional except for phased- TMDLs WLAs implemented through NPDES permits LAs implemented through voluntary and incentive based programs Monitoring and restoration information encouraged but not required unless the TMDL is phased Slide borrowed from USEPA

Conclusion Both TMDLs and WPPs try to reduce pollution and restore water quality Both use scientific tools in development Both provide estimates for pollutant loadings Both empower local stakeholders to have input into the plan Both are developed with cooperation with regional and local stakeholders

Questions? Kevin Wagner Texas Water Resources Institute Allen Berthold Texas Water Resources Institute