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7/29/2019 Water Quality Trading & Adaptive Management
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7/29/2019 Water Quality Trading & Adaptive Management
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Several options exist to meet WQBELs and TMDL allocations
including:
Adaptive Management Modifying wastewater treatment systems
Modifying your production process to limit additives or raw
materials
Trading
Options can be used in combination
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Water quality trading is an exchange
of pollutant reduction credits.
A buyer with a high pollutant controlcost can purchase pollutant reduction
or treatment from a willing seller.
Trading can produce substantial costsavings but must result in an
improvement in water quality and a
net reduction of the pollutant being
traded.
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Fox River Basin Developed guidance,
element list, issue summary,and reports.
Rock River Basin Developed a framework
and pursued some tradesbut lack of sufficienteconomic incentives prevent
trades.
Red Cedar Basin City of Cumberland Trade
Wisconsins History with Trading
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WQT May be Used To:
Demonstrate compliance with WQBELs
Offset pollutant load from new or expanding
discharger
WQT Guidance Not Applicable to TBELs
WQT not allowed when localized exceedance of
water quality standards will occur
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Nutrients Phosphorus
Nitrogen
Total Suspended Solids (sediment)
Temperature
Dissolved Oxygen-related Parameters (e.g.,biochemical oxygen demand)
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Non-TMDL WQBELs
Credits must be
generated upstream of
credit users discharge
TMDL WQBELs
Credits may begenerated within the
drainage area for the
impaired segment
(segmentshed)
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Credit threshold is the pollutant load below
which reductions must be made to generate
pollutant reduction credits.
Credits Generated by Point Source Threshold is lesser of WQBEL or TBEL
Credits Generated by Nonpoint Source Lesser of TMDL LA or Performance Standard (e.g., ch. NR 151)
5-yr Interim Credit = Reduction from Existing Pollutant Load
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Final Trade Ratio = Delivery + Equivalency + Reserve +
UncertaintyHabitat Adjustment
For trades involving point and nonpoint sources the trade
ratio cannot be lower than 1.2:1 (1.2 pounds of nonpoint for
every pound of point source pollutant). For trades located
upstream in the same HUC-12 the equation simplifies to:
Final Trade Ratio = 0.2 + UncertaintyHabitat Adjustment
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Delivery (distance between generator and user)
TMDLSame factors used in TMDL
Non-TMDLUSGS SPARROW model for P,
N and sediment
Equivalency (form of pollutant)
Not necessary with phosphorus Not yet specified for N and TSS (sediment)
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Downstream Trade Ratio Factor:
Percent Difference
between Buyers Loadand Total Load at
Point of Discharge
Downstream Trade
Ratio Factor
< 25% 0.2
25 - 50% 0.450 - 75% 0.6
75% > 0.8
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Reserve Factor
Reserve sets aside a portion of the pollutant credits to help
offset liability and uncertainty between the buyer and seller
associated with potential failure of management practices.
Pollutant / Constituent Reserve Factor
Total Phosphorus 0.2
Total Suspended Solids (TSS
or SSC)
0.2
Total Nitrogen Currently Not Available
Thermal Not Applicable
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BMP or Practice
Uncertainty Trading
Ratio
Applicable Technical
Standards
Schedule
for Credit
Use Notes
Whole Farm Managementwith multiple practices
1:1 Multiple This includes an approved nutrientmanagement plan, filter/buffer strips,
grassed water ways, conservation or no-till
tillage, and cover crops.
Conservation Easement 1:1 NRCS 327 Conservation
Cover
Credit for land out of production.
Companion Crops
(perennial vegetation)
1:1 Provides continuous protection to soil
surface.
Tillage
Mulch Till 3:1 NRCS 345 Mulch Till
No-Till 3:1 NRCS 329 No-till
Grassed Water Way 2:1 NRCS 412 Grassed
Waterway
Nutrient Management NRCS 590 Nutrient
ManagementFirst Trade Term:
Prior to Confirmation with
Soil Testing
4:1 Once it has been established through soil
testing that nutrient levels are dropping
and that the nutrient management plan is
being followed the trade ratio can be
lowered in subsequent permit/trade
cycles.
Second Trade
Term:Confirmation with Soil
Testing
3:1
Subsequent Trading Terms 2:1
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Habitat Adjustment Factor
NRCS Technical Standard Description
395 Stream Habitat andImprovement and Management
658 Wetland Creation
657 Wetland Restoration
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Final Trade Ratio = Delivery + Equivalency + Reserve +
UncertaintyHabitat Adjustment
For trades involving point and nonpoint sources the traderatio cannot be lower than 1.2:1 (1.2 pounds of nonpoint for
every pound of point source pollutant). For trades located
upstream in the same HUC-12 the equation simplifies to:
Final Trade Ratio = 0.2 + UncertaintyHabitat Adjustment
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Credits Generated by a Nonpoint Source SNAP-Plus and RUSLE2 for agricultural field practices
New Barnyard Toolworking with UW
SLAMM and P-8 for urban practices
Credits Generated by a Point Source Effluent monitoring
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Credits must be generated before they are used
Point source pollutant reduction must be measurable
BMP in-place and effective
Credit use timing depends on credit source
Point sourceAveraging period of limit
NonpointAnytime during calendar year
(highly variable discharge exception)
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Phosphorus WQBEL
Permit language allowing credits to be used when
demonstrating compliance with the limit
Reporting requirements for source and amount of credits
acquired Certification by permittee that BMPs are in place and are
effective
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DNR provides ground rules forbrokers and central exchange.
Credit user and generator may
use a contract.
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Oversight
1
Credit Generator Credit User
Credits Credits
http://dnr.wi.gov/7/29/2019 Water Quality Trading & Adaptive Management
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Compliance option focusing on water quality
improvements, rather than a phosphorus offset
Allows point sources to work with nonpoint sources toreduce overall phosphorus loads so that water quality
criteria can be attained
Interim Limits with extended compliance schedule.
NR 217.18, Wis. Adm. Code
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NOT an option for all point
sources
Specific eligibility requirements
must be met
NOT water quality trading
End of pipe compliance option
Eligibility Requirements
1. Receiving water exceeding
the WQC
2. NPS contribute >50% of P
load or NPS must be controlled
3. Filtration or equivalent
technology required to meetWQBEL
NOTE: MS4s considered nonpoint under
adaptive management
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Must use sound scientific data and rationale
PRESTO also available Calculates basin specific average annual phosphorus loads
from point and nonpoint sources
PRESTO combines three concepts: WatershedDelineation, Effluent Aggregation, and PollutantRunoff
Watershed
Delineation
Pollutant
Runoff
Effluent
Aggregation
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Eligible
Adaptive Management selected aspreferred option
Develop theAdaptive Management Plan
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NR 217.18(2)(d)
Step 1: Identify partners
Step 2: Describe the watershed and set loadreduction goals
Step 3: Conduct a watershed inventory
Step 4: Identify where reductions will occur
Step 5: Describe management measuresStep 6: Estimate load reductions expected by
permit term
Step 7: Measuring success
Step 8: Financial security
Step 9: Implementation schedule with milestones
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Point Sources
Partners to develop the plan County LWCDs
Consultants WDNR staff
Partners reducing P loads to receiving waters Agricultural producers
Non-permitted urban sources
MS4s
Other point sources
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Voluntary compliance options for WPDES permit
holders to comply with phosphorus requirements
Options will be used when it is economically
preferable to control nonpoint sources or other pointsources of P
Both require nonpoint and/or other point source
reductions
Contractual agreements should be made
Need to look in same watershed (HUC 12)
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Adaptive Management Trading
Pollutants Covered TP (and possibly TSS) All pollutants except
toxics
End Goals Attaining the water quality
criteria
Offsetting the limit
Implementation Area Watershed-focused Upstream-focused
Offsets No trade ratios Trade ratios apply
Timing Implemented throughout the
permit term
Generating credits
before they can be used
In-Stream Monitoring Required Not required
Level of Documentation
Needed
General watershed
information
Field-by-field
documentation
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