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Water Quality Trading

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Total Maximum Daily Loads (TMDLs) are the most common drivers for Water Quality Trading ... Oregon DEQ issued 'Internal Management Directive' on water quality trading ... – PowerPoint PPT presentation

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Title: Water Quality Trading


1
Water Quality Trading
  • Claire Schary
  • Water Quality Trading Coordinator
  • U.S. Environmental Protection Agency,
  • Region 10, Seattle, WA
  • schary.claire_at_epa.gov
  • (206) 553-8514
  • May 5, 2005

2
What is Water Quality Trading?
  • A source facing higher pollution reduction costs
    compensates another source for achieving
    equivalent, less costly reductions.
  • Market-based tool to solve water quality problems
  • Voluntary, flexible, stimulates innovation
  • Cost-effective pollution reduction
  • Operates within existing programs
  • Value for the pollution reduction credit is
    created by limiting the total amount of pollution
    allowed.

3
Conditions Necessary for Trading
  • Market Driver
  • regulatory requirement sets limit on pollutant
    discharges
  • defines commodity and market area
  • Cost differential
  • the financial incentive for entering into a trade
  • must cover transaction costs
  • Ability
  • technical feasibility and adequate supply
  • Opportunity
  • tools for trading available

4
Water Quality Trading TMDLs Are the Primary
Regulatory Drivers
  • Total Maximum Daily Loads (TMDLs) are the most
    common drivers for Water Quality Trading
  • TMDLs set a pollutant budget on all sources to
    achieve reductions necessary to achieve water
    quality standards in impaired water bodies
  • Under TMDLs point sources are assigned individual
    Waste Load Allocations
  • Enforced in NPDES permit through specified limit
  • Under TMDLs nonpoint sources are assigned Load
    Allocation by category
  • State, federal cost-share programs used to
    encourage use of Best Management Practices (BMPs)

5
EPA Region 10s Water Quality Trading Experience
  • Idaho
  • Lower Boise River Water Quality Trading
    Demonstration Project - phosphorus
  • Mid-Snake River Project - phosphorus
  • Idaho DEQ issued Water Pollutant Trading Guidance
    for Watersheds based on project experience
  • Oregon
  • Tualatin River - Clean Water Services Water
    Quality Trading Project temperature trading
    under watershed permit.
  • Oregon DEQ issued Internal Management Directive
    on water quality trading
  • Water Quality Trading Assessment Handbook

6
Lower Boise River
7
(No Transcript)
8
Phosphorus Trading Lower Boise River
  • Dynamic, market-based trading
  • Broad authorization to trade subject to trading
    rules
  • Liability remains with permit holder
  • PS, NPS sign private trade contracts
  • Environment protected
  • BMP List specifies acceptable practices,
    measurement
  • Location-based trade ratios applied to achieve
    environmentally equivalent reductions
  • Robust participation by agriculture
  • Trading driven by economic decisions
  • Private association oversees trading system
  • Mechanisms to support farm-scale and watershed
    scale participation

9
Phosphorus Trading Mid-Snake R.
  • Trades between point sources only (not enough
    supply from nonpoint sources so far)
  • Upstream point source City of Twin Falls has
    surplus phosphorus reductions
  • Downstream point source fish farmers need to make
    reductions
  • Trade reduction credits from Twin Falls will be
    used 30 miles downstream by fish farmers
  • Water quality is protected by
  • TMDLs overall phosphorus reduction requirement,
  • instream concentration limits, and
  • upper limits in fish farmers permits to prevent
    hot spots

10
Theory to Practice inWater Quality Trading
  • Not all pollutants are tradable commodities
  • Trading Policy allows nutrients, phosphorus,
    sediment, and case-by-case for others
  • Issues for pollutant trading suitability
  • Pollutant form Different forms of same pollutant
    discharged
  • Impact Fate and transport of pollutant, and its
    varying impact on sensitive portions of the
    watershed
  • Location of dischargers in the watershed for
    determining environmentally equivalent reductions
  • Time Match of timing of discharge and reductions
    across sources permit cycles
  • Quantity supply and demand must align

11
Financial Attractiveness of Water Quality
Trading
  • Need to determine if trading makes financial
    sense for one or more permittees in the
    watershed
  • TMDL allocations affect ability to trade
  • Cost of required reductions based on control
    technology options and lumpiness of reduction
    amounts achieved
  • Cost of incremental reduction amounts for
    individual sources are what drives the demand for
    trading
  • not the same as average cost of reductions
  • Assess potential control costs for other point
    sources, nonpoint sources in the watershed and
    identify potential trades
  • Consider transaction costs, risk, and alternative
    compliance strategies by other sources

12
Market Infrastructure to Support Trading
  • Transaction costs strongly influenced by market
    design, regulatory constraints, and uncertainty
    of outcomes
  • Participants uncertainty that a viable water
    quality trading market will develop
  • Participants uncertainty of regulatory approval
    of trades
  • Designing a market to address these needs, while
    matching the market size to the volume of trading
    expected, helps reduce transaction costs.

13
How Can Water Quality Trading Be Used to Improve
Multiple Resources?
  • One project can generate multiple types of
    credits
  • Depends on what is beneficial for other resources
  • Other types of credit markets need to define what
    is their baseline and then what is surplus for
    trading
  • Water Quality Trading Policy on baselines for
    credit calculations
  • Must be consistent with water quality standards
  • Must lead to reduction amounts that are equal to
    or greater than those established under existing
    regulatory requirements or under a TMDL.
  • When there is a TMDL, the Waste Load Allocations
    and Load Allocations are the baseline.

14
Question
  • For credits to be established for other ecosystem
    services besides water quality
  • What is the baseline and what is a surplus
    reduction?
  • How will environmental equivalency be established
    so the credit can be used in a different
    location?
  • Will there be sufficient demand and supply, and
    at the same time?
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