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ACWA Extreme Permit Makeover. Overview. Mixing zones: actual vs. regulatory ... The area in a receiving waterbody where a discharge undergoes initial dilution ... – PowerPoint PPT presentation

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Title: Ranei Nomura


1
Mixing Zone IMD UpdateDecember 1, 2005ACWA
Extreme Permit Makeover
  • Ranei Nomura
  • DEQ Water Quality Division
  • Surface Water Management
  • (503) 229-5657
  • nomura.ranei_at_deq.state.or.us

2
Overview
  • Mixing zones actual vs. regulatory
  • Background on regulatory mixing zones
  • DEQs upcoming mixing zone internal management
    directive
  • Bills in the 2005 Oregon Legislature
  • Next steps

3
BEFORE
4
AFTER
5
What is a mixing zone?
  • The area in a receiving waterbody where a
    discharge undergoes initial dilution and mixing.

6
What is a regulatory mixing zone?
For NPDES permits, a regulatory mixing zone is an
area defined in permit where
  • A discharge undergoes initial dilution and mixing
    in the receiving stream,
  • Water quality criteria are suspended or lessened
    provided several conditions are met, and
  • Despite the lowering of water quality criteria,
    the integrity and uses of the waterbody as a
    whole is protected.

7
Regulatory Mixing Zone
8
Regulatory Mixing Zone Components
Receiving waterbody
9
Effects within a mixing zone (EPA Handbook)
  • Concentrations above the chronic criteria are
    likely to prevent sensitive specifies from
    taking-up long-term residence in the mixing zone.
    Benthic and territorial organisms likely to be
    of greatest concern.
  • For organisms continuously residing within a
    mixing zone, survival, growth, and reproduction
    likely to be negatively affected.

10
Effects outside mixing zone (EPA Handbook)
  • If the total area affected by elevated
    concentrations within all mixing zones combined
    is small compared with the total area of a
    waterbody (such as a river segment), then mixing
    zones are likely to have little effect on the
    integrity of the water body as a whole, provided
    that they do not impinge on unique or critical
    habitats.

11
EPA rule and guidance for mixing zones
  • The federal Environmental Protection Agency (EPA)
    allows states to adopt their own mixing zone
    regulations as part of the states water quality
    standards (40 CFR 131.13) state regulations are
    subject to EPA approval.
  • EPA Guidance
  • Water Quality Standards Handbook, August 1994 (or
    Handbook)
  • Technical Support Document for Water
    Quality-based Toxics Control, March 1991 (or TSD)

12
EPA guidance
Allowable mixing zone characteristics should be
established to ensure that
  • Mixing zones do not impair the integrity of the
    water body as a whole,
  • There is no lethality to organisms passing
    through the mixing zone and
  • There are no significant health risks,
    considering likely pathways of exposure.

13
IMD Part 1 Allocating regulatory mixing zones
  • Allocation Process New vs. Renewal
  • Rule Requirements and Guidelines
  • Additional Considerations (e.g., anti-degradation
    policy, anti-backsliding, WET, general permits,
    etc.)
  • Assessing Regulatory Mixing Zones in the Field
  • Evaluation Report and Permit Language

14
IMD Part 1Renewal FAQs
  • There is no information in the previous
    evaluation report(s) on how the RMZ was
    developed. Can the existing RMZ be rolled over?
  • Will better documenting the existing RMZ, adding
    ZID language to the permit that was previously
    omitted, or making other similar changes during
    the renewal process require an in-depth
    antidegradation review?
  • Can an RMZ be re-oriented (described differently
    in the renewal permit as larger or smaller or in
    a different location due to new or better
    information) or an outfall be re-located?
  • Would increasing the size of an RMZ or ZID be
    considered backsliding and therefore prohibited
    by anti-backsliding regulations?

15
IMD Part 1 OAR requirements
  • Free of materials in concentrations that will
    cause acute toxicity to aquatic life. (A zone of
    immediate dilution where acute toxicity criteria
    may be allowed if it can be demonstrated that
    immediate dilution of the effluent within the
    mixing zone reduces toxicity below lethal
    concentrations.)
  • Free of materials the will settle to form
    objectionable deposits.
  • Free of floating debris, oil, scum, or other
    materials that cause nuisance conditions.
  • As small as feasible.

16
IMD Part 1 More OAR
  • Free of substances in concentrations that produce
    deleterious amounts of fungal or bacterial
    growths.
  • Avoid overlap with other mixing zones to the
    extent possible.
  • Be less than the total stream width as necessary
    to allow passage of fish and other aquatic
    organisms.
  • Minimize adverse effects on the indigenous
    biological community especially when species are
    present that warrant special protection.
  • Not threaten public health.

17
IMD Part 1 OAR for outside mixing zone
  • Be free of materials in concentrations that will
    cause chronic toxicity.
  • Meet all other water quality standards under
    normal annual low flow conditions.

18
Bottom Attachment
19
Bank Attachment
20
Fish Passage Issue
21
IMD Part 1 Evaluation report and permit language
  • Document in evaluation report
  • Regulatory mixing zone description
  • OAR 340-041-0053(2)(c) The limits of the mixing
    zone must be described in the wastewater
    discharge permit.
  • Catalogue of existing permit language in
    spreadsheet to be posted on intranet Permit
    Writers corner.

22
IMD Part 1 Permit language
  • Include length AND width
  • Describe shape (e.g., band, rectangular, radius,
    triangle, etc.)
  • Specify downstream or upstream if applicable
  • Note within 50 feet of outfall is a radius
  • Include description of ZID if applicable
  • The RMZ is that portion of the river contained
    within a band extending out 25 feet from the
    outfall to a point 10 feet upstream to 250 feet
    downstream of the outfall. The ZID is defined as
    that portion of the RMZ within 5 feet of the
    outfall.

23
IMD Part 1 Assessing RMZs in the field
  • Mixing/dilution studies
  • Bioassessments
  • When are they needed?
  • Close to critical or sensitive habitat,
  • In small receiving waters with little available
    dilution,
  • In areas where there are multiple mixing zones,
  • For allocation of a persistent bioaccumulative
    toxin (PBT), or
  • When whole effluent testing results indicate a
    potential problem with the effluent.

24
IMD Part 1 Bioassessments
25
IMD Part 2 Mixing zone study components
  • Environmental mapping
  • A map and characterization of the specific
    habitats, critical resource areas, and other
    beneficial uses of the receiving water.
  • Outfall and mixing zone characteristics
  • A description of the existing or proposed mixing
    zone, including a description of existing or
    proposed outfalls.
  • Ambient receiving water conditions
  • Discharge characteristics

26
IMD Part 2 Mixing zone study components,
continued
  • Mixing zone modeling analysis
  • Information on the model used, why it was
    selected over other models, and results of the
    modeling exercise. Results of the modeling
    exercise will predict available dilution in the
    receiving water.
  • Additional water quality data
  • Additional receiving water and discharge quality
    data will likely be needed to determine if the
    applicants discharge will comply with water
    quality standards, especially if it was not
    provided in the permit application or more data
    is needed.

27
IMD Part 2 Level of effort (e.g., ambient
receiving water conditions)
  • Level I, Simple
  • Estimates of average channel velocity based on
    assumptions regarding flow, depth,
    cross-sectional area, slope, and friction factors
    acceptable if actual data not available.
  • Level II, Moderate
  • Measurements of ambient velocity during critical
    and off-design conditions at a location
    representative of the average water column
    velocity desirable, but estimates acceptable.
    Detailed cross-sectional profile (width and
    depth) data is required if local velocities are
    estimated based on calculations.
  • Level III, Complex
  • Direct measurements of ambient velocity during
    critical and off-design conditions at multiple
    locations representative of water column velocity
    are necessary. Field data should be collected
    that depicts gradients in velocity dependent of
    stream morphometry (channel width and depth)
    relative to the mixing zone boundaries.

28
Decision Flow Chart for Determining Level of
Effort for Mixing Zone Study
29
IMD Part 2 Environmental mapping for Levels 1,
2, and 3
  • Plan view map delineating the existing or
    proposed mixing zones with length and width
    details.
  • Plan view map delineating areas within or near
    the mixing zone that provide unique habitat for
  • Shellfish harvesting
  • Wildlife dependent on waterbody (waterfowl,
    beaver, eagle, etc.)
  • Fish spawning and rearing, including cold water
    refugia and physical structures expected to
    attract fish (e.g., piers, irrigation intakes,
    outfalls, etc.)
  • Presence of threatened and endangered species
  • Drinking water intakes upstream or downstream
    within ½ mile
  • NPDES permittees upstream or downstream within ½
    mile
  • Other beneficial uses such as fishing, boating,
    or swimming

30
Cold Water Refugia
Structural Habitat
Outfall pipe
Regulatory Mixing Zone
Mixing Zone
Salmon Spawning Bed
Littoral Zone
31
IMD Part 2 Additional environmental mapping for
Level 3
  • Detailed salmonid TE use (e.g., spawning,
    holding, rearing, migratory pathways, etc.)
  • Measure of biologic integrity (i.e., rapid
    bioassessments, benthic surveys, etc.)
  • Fish migrations studies (example on next slide)
  • Thermal imagery e.g., Forward Looking Infrared
    (FLIR) camera technology
  • Maps illustrating channel width and depth and
    receiving water depth in the vicinity of the
    outfall
  • Published literature or agency reports in support
    of the environmental mapping

32
Fish Migration Study Detailed TE Salmonid Use
in the Lower Willamette River
33
Thermal Refugia using FLIR Imaging
34
2005 Oregon Legislature Senate Bill 555
  • Senate Bill 555
  • Sponsored by Senators Courtney and Ringo
  • Proposal to direct DEQ to condition discharge
    permits to prohibit discharge of toxic substances
    in amounts or concentrations that may be harmful
    to aquatic life or human health.
  • Exception if (permittee must pay DEQ for
    evaluation)
  • House Bill 2664
  • Sponsored by Representatives Schaufler and Jenson
  • Proposal to require person discharging wastes
    into waters of state to mark area with buoys,
    markers or signs if discharge causes waters to
    violate standards for water quality or purity.

35
Whats next?
  • Prepare final draft (manager and internal team
    reviews)
  • Develop implementation plan
  • Start of public review for at least 30 days
    likely for end of December 2005
  • Finalize in early spring
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