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Liz McKercher elizabeth.mckercher@deq.virginia.gov Craig Lott ...

Liz McKercher elizabeth.mckercher@deq.virginia.gov Craig Lott ...

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<strong>Liz</strong> <strong>McKercher</strong><br />

<strong>elizabeth</strong>.<strong>mckercher@deq</strong>.<strong>virginia</strong>.<strong>gov</strong><br />

<strong>Craig</strong> <strong>Lott</strong><br />

craig.lott@deq.<strong>virginia</strong>.<strong>gov</strong>


�Definition �Definition and Background<br />

�TMDL development process<br />

�Incorporating �Incorporating Construction Stormwater<br />

Discharges: Past and Present<br />

�TMDL �TMDL-Stormwater Stormwater Universe in Virginia<br />

�Presentation �Presentation Goal: Provide the RAP with<br />

sufficient information to construct<br />

regulatory language


�� Federal Clean Water Act, Act Section 303(d)<br />

• List impaired waters, develop TMDLs<br />

� 40 CFR Section § 130.7<br />

• Water Quality Planning and Management<br />

• TMDLs shall take into account critical conditions for<br />

stream t flow, fl lloading, di and d water t quality lit parameters t<br />

� Code of Virginia,<br />

• §62 §62.1-44.15 1-44 15 (10) & (23) and §62 §62.1-44.19:4 1-44 19:4 and 19:8<br />

� Water Quality Management Planning<br />

Regulation egu at o (9 VVAC-25-720) C 5 0)


1972 1999 2010 2014-15<br />

Clean Water<br />

Act 303(d)<br />

•Each State shall<br />

establish for the<br />

waters identified<br />

...the total maximum<br />

daily load<br />

Settlement by<br />

EPA, Consent<br />

Decree (CD)<br />

•To meet the CD,<br />

Vi Virginia i i completed l t d<br />

TMDLs covering<br />

approximately 225<br />

shellfish and 333<br />

non-shellfish<br />

impairments<br />

TMDL<br />

development<br />

continues<br />

post-CD<br />

• Over 1,100<br />

additional waters<br />

require TMDLs<br />

• 100 TMDLs per<br />

biennium<br />

expected<br />

2002<br />

Clarification from EPA on NPDES-<br />

regulated storm water discharges as<br />

wasteload allocation<br />

EPA modifies<br />

watershed<br />

cleanup<br />

performance<br />

measures<br />

• Begin giving<br />

credit for non-<br />

TMDL solutions<br />

• TMDLs still one<br />

watershed t h d clean- l<br />

up tool


�Maximum load of a specified pollutant<br />

that a water body can assimilate and<br />

attain water quality standards<br />

�Includes a wasteload allocation (point<br />

sources), load allocation (non-point<br />

sources) and a margin of safety.


�TMDL �TMDL = WLA + LA + MOS


�40 �40 CFR '122 122.44(d)(1)(vii)(B), 44(d)(1)(vii)(B) “Effluent Effluent<br />

limits developed to protect a narrative<br />

water quality criterion, criterion a numeric water<br />

quality criterion, or both, are consistent<br />

with assumptions and requirements of<br />

any available WLA for the discharge<br />

prepared by the State and approved by<br />

EPA pursuant to 40 CFR '130.7.”


� Benthic Impairment<br />

• Water body not fully supporting its uses due to water<br />

quality violations of the general aquatic life (benthic)<br />

standard.<br />

�� Aquatic Life Standard<br />

• Based on the aquatic, benthic (or bottom‐dwelling)<br />

macroinvertebrates (organisms without backbones<br />

that t atca can be seen see with w t the t enaked a ed eye) tthat at form o tthe e<br />

foundation of a stream’s food chain.<br />

� The aquatic life water quality standard<br />

states that all state waters should support a<br />

healthy and diverse community of bugs and<br />

fish.


EVALUATE WATERSHED AND<br />

IMPAIRMENT<br />

Water quality data, stressors/sources, climatic conditions, soils,<br />

watershed land use, model existing conditions.<br />

Stakeholder Input<br />

IDENTIFY ENDPOINT<br />

St Stakeholder k h ld IInput t<br />

Water Quality Standards or Reference Condition<br />

MODEL SCENARIOS<br />

Determine allocation of the load among point sources and non-<br />

point i t sources and d allow ll for f a margin i of f safety, f t and d future f t growth. th<br />

Identify reductions.<br />

Stakeholder Input


�Model framework:<br />

• General Watershed Loading Function (GWLF) or<br />

Hydrologic Simulation Program Fortran (HSPF)<br />

�Source Assessment:<br />

• Quantify Construction Storm Load from permits<br />

queried and stakeholder input<br />

�Waste load allocation


�Construction �Construction loads – not clearly<br />

distinguished as a point source (~2004)<br />

�Future �Future activities not explicitly discussed


� Identify y Construction Stormwater as a ppoint<br />

source<br />

• Some TMDLS aggregate the construction load with<br />

that of the MS4<br />

� Allow for future growth in Construction<br />

Stormwater permitted activities (~2011)<br />

�� Differentiate between in-stream loads and<br />

land-based<br />

� Often differentiate between activities within<br />

and d outside t id of f MS4 boundary b d<br />

� By 2011, 48 TMDLs for sediment, 9 for<br />

Phosphorus p , ,pplus the Bay ywatershed


�Many �Many point source permits listed<br />

�Some point sources given an individual<br />

WLA (e.g. (e g waste water treatment plant)<br />

�Others given an aggregated WLA by<br />

source category (e.g. (e g construction)


� Benthic TMDL Watersheds Sediment,<br />

Nitrogen, Phosphorus, including TSS for<br />

the Chesapeake Bay<br />

� Local watershed TMDLs in Virginia where<br />

th the equation ti address dd TSS and d TDS have h<br />

addressed mining sources<br />

� pH TMDL studies to date result in<br />

recommendation for swamp waters<br />

designation designation, or there are co co-pollutants pollutants


Six TMDLs Requiring Additional Measures<br />

TMDL Name Pollutant Total Reductions*<br />

Goose Creek Sediment 70%<br />

Mossy Creek Sediment 74.9%<br />

Mill Creek Watershed Sediment 69‐73%<br />

Bull Run Sediment 77 77.37% 37%<br />

Rivanna River Watershed Sediment 0/59.3%<br />

Outside of MS4/Inside MS4<br />

Difficult Run Sediment 73%<br />

*Reductions to a site with no management/no E&S.


2003 TMDLs - Interpreted to Require<br />

Additional Measures<br />

TMDL Name Pollutant Total Reductions*<br />

Blacks Run Watershed sediment 70%<br />

Cooks Creek Watershed<br />

sediment & Phosphorus 90%<br />

Mill Creek Watershed sediment 70%<br />

Pleasant Run Watershed sediment 80%<br />

Pleasant Run Watershed Phosphorus 80%<br />

Holmans Run sediment 70%<br />

*Reductions to a site with no management/no g /<br />

E&S.


http://www.deq.<strong>virginia</strong>.<strong>gov</strong>/ConnectWithDEQ/VEGIS/VEGISDatasets.aspx


http://www.deq.<strong>virginia</strong>.<strong>gov</strong>/Programs/Water/WaterQualityInformationTMD<br />

Ls/TMDL/TMDLDevelopment/ApprovedTMDLReports.aspx


http://www.deq.<strong>virginia</strong>.<strong>gov</strong>/Programs/<br />

Water/WaterQualityInformationTMDLs/T<br />

MDL/TMDLImplementation/TMDLImple<br />

mentationPlans.aspx


� B.Limitation on coverage. g<br />

� TMDL limitation. Discharges to waters for which a<br />

wasteload allocation (WLA) for a pollutant has<br />

been established in a "total maximum daily y load"<br />

(TMDL) approved by the State Water Control<br />

Board that would apply to stormwater discharges<br />

from o a co construction st uct o act activity v ty are a enot ot eligible e g b e for o<br />

coverage under this permit unless the<br />

stormwater pollution prevention plan (SWPPP)<br />

developed by the operator is consistent with the<br />

requirements related to TMDLs contained in<br />

Section II D 6.


�� 6. Total maximum daily loads. A total<br />

maximum daily load (TMDL) approved by<br />

the State Water Control Board may include a<br />

wasteload allocation to the regulated<br />

construction activity that identifies the<br />

pollutant for which stormwater control<br />

measures are necessary f for the h surface f<br />

waters to meet water quality standards. The<br />

pollutant po uta t identified de t ed in a wasteload waste oad allocation a ocat o<br />

as of the effective date of this permit must<br />

be specified in the SWPPP……


� The SWPPP shall include strategies g and control<br />

measures to ensure consistency with the<br />

assumptions and requirements of the TMDL WLA<br />

that apply to the operator's discharge. In a<br />

situation i i where h a TMDL has h specified ifi d a general l<br />

wasteload allocation applicable to construction<br />

stormwater discharges, but no specific requirements<br />

for construction sites have been identified in the<br />

TMDL, the operator shall consult with the state or<br />

federal TMDL authority to confirm that meeting<br />

permit requirements will be consistent with the<br />

approved TMDL. If the TMDL specifically precludes<br />

such discharges, the operator is not eligible for<br />

coverage under the general permit.


� Erosion and Sediment Control Plans and<br />

Stormwater Management Plans required under<br />

the general permit (with the exception of those<br />

plans p for sites previously p y covered under a<br />

previous version of the general permit) shall<br />

include a written explanation demonstrating that<br />

the t epa plan addessest addresses these eseccritical tca po points tsoof<br />

interest in addition to the basic elements<br />

included in those plans:<br />

� i. Protection measures for discharges to the<br />

� i. Protection measures for discharges to the<br />

Chesapeake Bay or impaired waters or<br />

� waters with an established TMDL.


� Part V. CONSISTENCY WITH TOTAL MAXIMUM<br />

DAILY LOADS<br />

� If the discharge covered by this permit enters a<br />

water with an established or approved Total<br />

MMaximum i<br />

� Daily Load (TMDL), the permittee must implement<br />

measures to ensure that the discharge of pollutants<br />

�� from the site is consistent with the assumptions and<br />

meets the requirements of the approved TMDL,<br />

� including any specific wasteload allocation that has<br />

been established that would apply to the discharge discharge.

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