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EPA

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EPA s New Rule for Cooling Water Intake Structures at Existing (Phase II) Facilities Kristy A.N. Bulleit Hunton & Williams 1900 K Street, N.W. – PowerPoint PPT presentation

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Title: EPA


1
EPAs New Rule for Cooling Water Intake
Structures at Existing (Phase II) Facilities
Kristy A.N. BulleitHunton Williams1900 K
Street, N.W.Washington, DC 20006 202-955-1547
kbulleit_at_hunton.com
James N. Christman and Elizabeth E. Aldridge
Hunton WilliamsRiverfront Plaza, East Tower,
951 East Byrd Street Richmond, VA
23219 804-788-8368 jchristman_at_hunton.com 804-788
-8549 ealdridge_at_hunton.com
2
Background
  • Phase II rule for existing facilities was signed
    February 16, 2004
  • To be published in the Federal Register in about
    mid-March 2004
  • Becomes final for judicial review purposes two
    weeks after publication in the Federal Register

3
Background
  • On February 3, 2004, the Second Circuit Court of
    Appeals ruled that restoration cannot be used for
    new (Phase I) facilities
  • Nevertheless, EPA decided to allow restoration in
    the Phase II rule, but limited the circumstances
    under which it can be used.

4
Applies to a Facility If
  • Primary activity is to generate and transmit
    electric power or to generate electric power for
    sale to a different entity for transmission
  • Has a total design intake flow ? 50 MGD
  • Uses ? 25 of water withdrawn exclusively for
    cooling purposes
  • Commenced construction on or before January 17,
    2002

5
Adding New Units
  • Existing facility includes any modification of
    or addition of a unit at an existing facility
    that is not a new facility ( 125.83)
  • An existing facility that adds a new generating
    unit at the same site for repowering and
    concurrently increases the design capacity of its
    intake structure or adds a new intake structure
    where it did not previously have one (when
    converting a gas turbine to a combined cycle
    unit, for example) is an existing facility

6
Existing Facility Includes
  • New units added to a facility for purposes of the
    same general industrial operation
  • EPA does not want to discourage upgrades,
    modifications, or repowering that would increase
    energy efficiency or supply

7
The Rule in a NutshellTwo Performance Standards
  • Calculate baseline
  • Reduce impingement mortality 80-90 from baseline
  • Also reduce entrainment 60-90 if
  • Capacity utilization ? 15 (not a peaking unit)
    and either
  • Withdrawn water from tidal river, estuary, ocean,
    or Great Lakes or
  • Design intake flow withdraws gt 5 of mean annual
    flow of freshwater river or stream

8
Capacity Utilization Rate
  • Ratio of average annual net generation (in MWh)
    and total net capability to generate power (in
    MW) multiplied by number of hours during year.
  • If facility has multiple CWIS and each structure
    serves a separate unit or group of units, CWIS
    capacity utilization rate may be calculated
    separately.

9
Capacity Utilization Rate (contd)
  • Measured over representative 5 year period,
    unless plant commits to remain below 15
  • Only applies to steam units

10
Five Ways to Comply
  • Cooling water flow commensurate with a
    closed-cycle recirculating system
  • -- Maximum through-screen design intake
    velocity of 0.5 ft/s meets impingement mortality
    standard only
  • Demonstrate that existing intake reduces
    impingement mortality 80-95 from a calculation
    baseline and, for some plants, reduces
    entrainment 60-90

11
Five Ways to Comply (contd)
  • Reduce impingement mortality 80-95 and, for some
    plants, reduce entrainment by 60-90 using
  • - Design and construction technologies
  • - Operational measures
  • - Restoration, in some cases
  • In freshwater rivers and streams, use cylindrical
    wedge-wire screens meeting conditions in
    125.99(a)(1)
  • - Or a technology-approved by the state that
    can consistently meet the performance standards
    in the state

12
Conditions for Wedge-wire Screens
  • Freshwater river or stream
  • Sufficient ambient counter currents to promote
    cleaning of screen face
  • Maximum through-screen design intake velocity?
    0.5 ft/s
  • Slot size appropriate for eggs, larvae, and
    juveniles at site
  • Entire main condenser cooling water flow directed
    through the screens (except small flows lt 2 MGD
    for auxiliary plant cooling)

13
Five Ways to Comply (contd)
  1. Site-specific requirements under the cost-cost or
    cost-benefit test

14
Applying the Performance Standards
  • Calculation baseline Estimate of impingement
    mortality and entrainment that would occur
    assuming
  • Cooling water system designed as once-through
  • Opening located at the shoreline near the water
    surface
  • 3/8-inch mesh traveling screen parallel to the
    shoreline
  • No controls implemented in whole or in part for
    the purpose of reducing impingement mortality and
    entrainment.

15
Applying the Performance Standards
  • EPA intends to allow credit for
  • Angled screen face to guide organisms away from
    intake structure
  • Opening place in water column instead of at
    surface
  • Any structural or operational controls used in
    whole or part to reduce impingement mortality or
    entrainment
  • As built baseline assessment also allowed.

16
Special Provisions forLakes and Reservoirs
  • If you withdraw cooling water from a lake
  • (other than the Great Lakes) or reservoir,
  • and you propose to increase the design intake
    flow,
  • then, increased flow must not disrupt the
    natural thermal stratification or turnover
    pattern
  • unless the disruption does not adversely affect
    management of fisheries

17
Interpreting thePerformance Standards
  • Permit writer has significant discretion as to
    how the performance standards are applied in the
    permit
  • Permit writer may determine that all species must
    be considered or only representative species
  • Permit writer averaging period apparently can be
    up to a full five-year permit term (see preamble
    p. 163)

18
Exceptions for Excessive Costs
  • Rule offers cost-cost test and cost-benefit
    test
  • If your costs are significantly greater, you
    can get site-specific requirements

19
Cost-Cost Test
  • Six-step process prescribed
  • Determine what technology EPA used for your
    facility
  • Use EPAs costing equation to calculate
    annualized capital and net operation and
    maintenance costs for a facility with your design
    intake flow using the technology chosen by EPA

20
Cost-Cost Test (contd)
  • Calculate your own costs and show that they are
    significantly greater than the costs estimated
    by EPAs method
  • Significantly is not defined

21
Cost-Benefit Test
  • Cost of compliance must be significantly greater
    than the benefits of complying
  • While entrainment survival is not part of
    performance standard, it may be considered
    through application of cost-benefit test.

22
Costs and Benefits
  • EPA has retreated from some of its worst
    cost-benefit methods
  • 50 rule for non-use benefits
  • Habitat replacement cost analysis of benefits
  • Societal revealed preference analysis for
    threatened and endangered species

23
Benefits Valuation Study Requirments
  • Describe methodology
  • Develop valuation estimates
  • Document assumptions
  • Analyze sources of uncertainty
  • Arrange for peer review (consulting resource
    agencies about peer reviewers)
  • Describe non-monetized benefits

24
What Site-Specific Requirements?
  • The site-specific alternative technology must
    achieve an efficacy that is
  • As close as practicable to the applicable
    performance standards
  • Without resulting in costs that are significantly
    greater than the EPA costs or the calculated
    benefits at your facility

25
Operational Measures
  • You may meet the performance standards by
    operational measures
  • Reductions in cooling water intake flow
  • Variable speed pumps
  • Seasonal flow reductions or shutdowns
  • More frequent rotation of traveling screens

26
Restoration
  • Restoration can be used only if permittee first
    shows that design and construction
    technologies/operational measures are less
    feasible, less cost-effective, or less
    environmentally desirable.
  • Restoration results must be substantially similar
    to performance standards or site-specific
    alternative.
  • Restoration Plan may focus on species of concern
    to resources agencies.

27
Application Requirements
  • All plants must submit source waterbody physical
    data, CWIS data, and cooling system data
  • Plants that neither have nor propose to install
    closed-cycle cooling will have to perform and
    submit a Comprehensive Demonstration Study (CDS)
    (unless plant has design velocity lt 0.5 ft./s and
    is subject only to impingement requirements, in
    which case no CDS required).

28
Application Requirements (contd)
  • CDS components depend on specific compliance
    option chosen.
  • Unless facility plans to show it already meets
    performance standards, all CDS start with
    submission of Proposal for Information Collection
    to permit writer

29
Application Requirements (cont)
  • Other CDS components may include
  • Source waterbody flow information
  • Impingement Mortality and/or Entrainment
    Characterization Study
  • Technology and Compliance Assessment Information,
    which may include
  • Design and Construction Technology Plan
  • Technology Installation and Operation Plan

30
TIOP
  • The Technology Installation and Operation Plan
    describes how you will install, operate, monitor,
    and maintain the intake technology and adaptive
    management steps to take if the technology does
    not perform as expected.
  • TIOP is crucial, because permittee may request
    that TIOP compliance compliance with rule.
  • If permittee fails to comply with performance
    standard but meets TIOP, it may request
    site-specific alternative requirements.

31
Application Requirements (contd)
  • Restoration Plan (if appropriate)
  • Information to Support Site-specific
    Determination of BTA, including
  • Comprehensive Cost Evaluation Study
  • Valuation of Monetized Benefits of Reducing
    (IME) (cost-benefit test only)
  • Site-specific Technology Plan
  • Verification Monitoring Plan (including proposal
    for identifying moribund fish)

32
When Must You Comply?
  • Submit the information with the next permit
    application
  • If your permit expires lt 4 years after
    publication, you may ask to submit the
    information up to 3 ½ years after publication of
    the rule in the Federal Register

33
Permit Renewals After the First
  • In permit terms after the first, you may ask that
    compliance and restoration be based on compliance
    with the Technology Installation and Operation
    Plan and Restoration Plan
  • One year before permit expiration, if you are in
    compliance with your TIOP and/or performance
    standards, you may request reduced data
    requirements for permit renewal.
  • Permit writer may change requirements at each
    permit renewal

34
Cooling Ponds
  • EPA does not intend to change the regulatory
    status of cooling ponds
  • Cooling ponds are waters of the U.S. if they
    meet the definition

35
State-Approved Alternatives and Reserve State
Authority
  • State may have functionally equivalent program
  • Must produce results comparable to EPAs
    performance standards
  • Permit writer may establish more stringent
    requirements if EPAs rule would not meet the
    requirements of state law or other federal law

36
Trading
  • State may adopt trading programs
  • Must be within the same watershed
  • May trade fish for fish but not pollutants for
    fish

37
Nuclear Safety
  • If the EPA rule would conflict with an NRC safety
    requirement, you can have site-specific
    requirements
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