Virginia Administrative Code
Database updated through March 17, 2010
9VAC25-720-10. Definitions.
The following words and terms when used in this chapter shall
have the following meanings unless the context clearly indicates otherwise:
"Assimilative capacity" means the greatest amount of
loading that a water can receive without violating water quality standards,
significantly degrading waters of existing high quality, or interfering with
the beneficial use of state waters.
"Best management practices (BMP)" means a schedule
of activities, prohibition of practices, maintenance procedures and other
management practices to prevent or reduce the pollution of state waters. BMPs
include treatment requirements, operating and maintenance procedures, schedule
of activities, prohibition of activities, and other management practices to
control plant site runoff, spillage, leaks, sludge or waste disposal, or
drainage from raw material storage.
"Best practicable control technology currently available
(BPT)" means control measures required of point source discharges (other
than POTWs) as determined by the EPA pursuant to § 304(b)(1) of the CWA (33 USC
§ 1251 et seq.) as of 1987.
"Board" means the State Water Control Board (SWCB).
"Chesapeake Bay Watershed" means the following
Virginia river basins: Potomac River Basin (9VAC25-260-390 and 9VAC25-260-400),
James River Basin (9VAC25-260-410, 9VAC25-260-415, 9VAC25-260-420, and
9VAC25-260-430), Rappahannock River Basin (9VAC25-260-440), Chesapeake Bay and
small coastal basins (9VAC25-260-520, Sections 2 through 3g), and the York
River Basin (9VAC25-260-530).
"Clean Water Act or Act (CWA)" means 33 USC § 1251 et
seq. as amended, as of 1987.
"Delivery factor" means an estimate of the number of
pounds of total nitrogen or total phosphorus delivered to tidal waters for
every pound discharged from a permitted facility, as determined by the specific
geographic location of the permitted facility, to account for attenuation that
occurs during riverine transport between the permitted facility and tidal
waters. Delivery factors shall be calculated using the Chesapeake Bay Program
watershed model.
"Discharge" means when used without qualification, a
discharge of a pollutant or any addition of any pollutant or combination of
pollutants to state waters or waters of the contiguous zone or ocean or other
floating craft when being used for transportation.
"Effluent limitation" means any restriction imposed
by the board on quantities, discharge rates or concentrations of pollutants
that are discharged from point sources into state waters.
"Effluent limitation guidelines" means a regulation
published by EPA under the Act and adopted by the board.
"Effluent limited segment (EL)" means a stream
segment where the water quality does and probably will continue to meet state
water quality standards after the application of technology-based effluent
limitations required by §§ 301(b) and 306 of the CWA (33 USC § 1251 et seq.) as
of 1987.
"Environmental Protection Agency (EPA)" means the
United States Environmental Protection Agency.
"Equivalent load" means 2,300 pounds per year of
total nitrogen and 300 pounds per year of total phosphorus at a flow volume of
40,000 gallons per day; 5,700 pounds per year of total nitrogen and 760 pounds
per year of total phosphorus at a flow volume of 100,000 gallons per day; and
28,500 pounds per year of total nitrogen and 3,800 pounds per year of total
phosphorus at a flow volume of 500,000 gallons per day.
"Load or loading" means the introduction of an
amount of matter or thermal energy into a receiving water. Loading may be
either man-caused (pollutant loading) or natural (background loading).
"Load allocation (LA)" means the portion of a
receiving water's loading capacity attributable either to one of its existing
or future nonpoint sources of pollution or to natural background sources. Load
allocations are best estimates of the loading, which may range from accurate
estimates to gross allotments, depending on the availability of data and
appropriate techniques for predicting the loading. Wherever possible, natural
and nonpoint source loads should be distinguished.
"Nonpoint source" means a source of pollution, such
as a farm or forest land runoff, urban storm water runoff, mine runoff, or salt
water intrusion that is not collected or discharged as a point source.
"Point source" means any discernible, defined and
discrete conveyance, including but not limited to any pipe, ditch, channel,
tunnel, conduit, well, discrete fissure, container, rolling stock vessel or other
floating craft, from which pollutants are or may be discharged. This term does
not include return flows from irrigated agricultural land.
"Pollutant" means any substance, radioactive
material, or heat that causes or contributes to, or may cause or contribute to,
pollution. It does not mean:
1. Sewage from vessels; or
2. Water, gas, or other material that is injected into a well
to facilitate production of oil, dry gas, or water derived in association with
oil or gas production and disposed of in a well, if the well is used either to
facilitate production or for disposal purposes if approved by the Department of
Mines, Minerals and Energy unless the board determines that such injection or
disposal will result in the degradation of ground or surface water resources.
"Pollution" means such alteration of the physical,
chemical or biological properties of any state waters as will or is likely to
create a nuisance or render such waters (i) harmful or detrimental or injurious
to the public health, safety or welfare, or to the health of animals, fish or
aquatic life; (ii) unsuitable with reasonable treatment for use as present or
possible future sources of public water supply; or (iii) unsuitable for
recreational, commercial, industrial, agricultural, or other reasonable uses;
provided that: (a) an alteration of the physical, chemical, or biological
property of state waters, or a discharge or deposit of sewage, industrial
wastes or other wastes to state waters by any owner, which by itself is not
sufficient to cause pollution, but which, in combination with such alteration
of or discharge or deposit to state waters by other owners is sufficient to
cause pollution; (b) the discharge of untreated sewage by any owner into state waters;
and (c) contributing to the contravention of standards of water quality duly
established by the board, are "pollution" for the terms and purposes
of this water quality management plan.
"Publicly owned treatment works (POTW)" means any
sewage treatment works that is owned by a state or municipality. Sewers, pipes,
or other conveyances are included in this definition only if they convey
wastewater to a POTW providing treatment.
"Significant discharger" means (i) a point source
discharger to the Chesapeake Bay watershed with a design capacity of 0.5
million gallons per day or greater, or an equivalent load; (ii) a point source
discharger to the Chesapeake Bay watershed downstream of the fall line with a
design capacity of 0.1 million gallons per day or greater, or an equivalent
load; (iii) a planned or newly expanding point source discharger to the
Chesapeake Bay watershed that is expected to be in operation by 2010 with a
permitted design of 0.5 million gallons per day or greater, or an equivalent
load; or (iv) a planned or newly expanding point source discharger to the
Chesapeake Bay watershed downstream of the fall line with a design capacity of
0.1 million gallons per day or greater, or an equivalent load, that is expected
to be in operation by 2010.
"State waters" means all waters, on the surface and
under the ground and wholly or partially within or bordering the Commonwealth
or within its jurisdiction, including wetlands.
"Surface water" means all waters in the Commonwealth
except ground waters as defined in § 62.1-255 of the Code of Virginia.
"Total maximum daily load (TMDL)" means the sum of
the individual waste load allocations (WLAs) for point sources, load
allocations (LAs) for nonpoint sources, natural background loading and usually
a safety factor. TMDLs can be expressed in terms of either mass per time,
toxicity, or other appropriate measure. The TMDL process provides for point
versus nonpoint source trade-offs.
"Toxic pollutant" means any agent or material
including, but not limited to, those listed under § 307(a) of the CWA (33 USC
§ 1251 et seq. as of 1987), which after discharge will, on the basis of
available information, cause toxicity.
"Toxicity" means the inherent potential or capacity
of a material to cause adverse effects in a living organism, including acute or
chronic effects to aquatic life, detrimental effects on human health or other
adverse environmental effects.
"Virginia Pollution Discharge Elimination System (VPDES)
permit" means a document issued by the board, pursuant to 9VAC25-31,
authorizing, under prescribed conditions, the potential or actual discharge of
pollutants from a point source to surface waters.
"Waste load allocation (WLA)" means the portion of a
receiving water's loading or assimilative capacity allocated to one of its
existing or future point sources of pollution. WLAs are a type of water
quality-based effluent limitation.
"Water quality limited segment (WQL)" means any
stream segment where the water quality does not or will not meet applicable
water quality standards, even after the application of technology-based
effluent limitations required by §§ 301(b) and 306 of the CWA (33 USC § 1251 et
seq. as of 1987).
"Water quality management plan (WQMP)" means a
state- or area-wide waste treatment management plan developed and updated in
accordance with the provisions of §§ 205(j), 208 and 303 of the CWA (33 USC
§ 1251 et seq. as of 1987).
"Water quality standards (WQS)" means narrative
statements that describe water quality requirements in general terms, and of numeric
limits for specific physical, chemical, biological or radiological
characteristics of water. These narrative statements and numeric limits
describe water quality necessary to meet and maintain reasonable and beneficial
uses such as swimming and, other water based recreation, public water supply
and the propagation and growth of aquatic life. The adoption of water quality
standards under the State Water Control Law is one of the board's methods of
accomplishing the law's purpose.
Statutory Authority
§ 62.1-44.15 of the Code of Virginia; § 303 of the federal Clean
Water Act.
Historical Notes
Derived from Virginia Register Volume 19, Issue 14, eff. April
24, 2003; amended, Virginia Register Volume 22, Issue 3, eff. November 16,
2005.
9VAC25-720-20. Purpose.
The purpose of this regulation is to list by major river basin the following:
EPA-approved and board-adopted total maximum daily loads (TMDLs) and the
stream segment classifications, effluent limitations including water quality
based effluent limitations, and waste load allocations contained in the
existing water quality management plans (WQMPs).
Statutory Authority
§ 62.1-44.15 of the Code of Virginia and 33 USC § 1313(e) of the Clean Water
Act.
Historical Notes
Derived from Virginia Register Volume 19, Issue 14, eff. April 24, 2003.
9VAC25-720-30. Relationship to 9VAC25-40, Regulation for Nutrient Enriched
Waters and Dischargers within the Chesapeake Bay Watershed.
The provisions of this chapter and 9VAC25-40, Regulation for Nutrient Enriched
Waters and Dischargers within the Chesapeake Bay Watershed, constitute the
nutrient reduction requirements for point source discharges in the Chesapeake
Bay Watershed to protect the Chesapeake Bay and its tidal rivers.
Statutory Authority
§ 62.1-44.15 of the Code of Virginia; § 303 of the federal Clean Water Act.
Historical Notes
Derived from Virginia Register Volume 22, Issue 3, eff. November 16, 2005.
9VAC25-720-40. Implementing Nitrogen and Phosphorus Waste Load
Allocations in the Chesapeake Bay Watershed.
A. Nitrogen and phosphorus waste load allocations assigned to
individual significant dischargers in 9VAC25-720-50 C, 9VAC25-720-60 C,
9VAC25-720-70 C, 9VAC25-720-110 C, and 9VAC25-720-120 C may be exchanged in
accordance with the Chesapeake Bay Watershed Nutrient Credit Exchange Program
established under Article 4.02 (§ 62.1-44.19:12 et seq.) of Chapter 3.1 of Title
62.1 of the Code of Virginia. Exchanges must account for the delivery factor
applicable to each discharge based upon its location within the river basin and
calculated by the Chesapeake Bay Program watershed model.
B. The nitrogen and phosphorus waste load allocations assigned
to individual significant dischargers in 9VAC25-720-50 C, 9VAC25-720-60 C,
9VAC25-720-70 C, 9VAC25-720-110 C, and 9VAC25-720-120 C are considered to be
bioavailable to aquatic life. On a case-by-case basis, a discharger may
demonstrate to the satisfaction of the board that a significant portion of the
nutrients discharged by the facility is not bioavailable to aquatic life. In
these cases, the board may limit the permitted discharge to reflect only that
portion of the assigned waste load allocation that is bioavailable. Such limits
shall be consistent with the assumptions and methods used to derive the
allocations through the Chesapeake Bay watershed and water quality models.
C. Unless otherwise noted, the nitrogen and phosphorus waste
load allocations assigned to individual significant dischargers in
9VAC25-720-50 C, 9VAC25-720-60 C, 9VAC25-720-70 C, 9VAC25-720-110 C, and
9VAC25-720-120 C are considered total loads including nutrients present in the
intake water from the river, as applicable. On a case-by-case basis, an
industrial discharger may demonstrate to the satisfaction of the board that a
significant portion of the nutrient load originates in its intake water. In
these cases, the board may limit the permitted discharge to reflect only the
net nutrient load portion of the assigned waste load allocation. Such limits
shall be consistent with the assumptions and methods used to derive the
allocations through the Chesapeake Bay watershed and water quality models.
D. The board may amend this regulation to adjust individual
nitrogen and phosphorus waste load allocations. Reasons for considering such an
adjustment include, but are not limited to:
1. A discharger completes or does not complete a plant
expansion as evidenced by issuance of a Certificate To Operate by December 31,
2010; or
2. A river basin nutrient load allocation is not achieved.
Any adjustment to an individual waste load allocation must
ensure water quality standards are maintained.
Statutory Authority
§ 62.1-44.15 of the Code of Virginia; § 303 of the federal Clean
Water Act.
Historical Notes
Derived from Virginia Register Volume 22, Issue 3, eff.
November 16, 2005.
9VAC25-720-50. Potomac-Shenandoah River Basin.
A. Total Maximum Daily Load (TMDLs).
TMDL #
|
Stream Name
|
TMDL Title
|
City/County
|
WBID
|
Pollutant
|
WLA
|
Units
|
1.
|
Muddy Creek
|
Nitrate TMDL Development for Muddy Creek/Dry River, Virginia
|
Rockingham
|
B21R
|
Nitrate
|
49,389.00
|
LB/YR
|
2.
|
Blacks Run
|
TMDL Development for Blacks Run and Cooks Creek
|
Rockingham
|
B25R
|
Sediment
|
32,844.00
|
LB/YR
|
3.
|
Cooks Creek
|
TMDL Development for Blacks Run and Cooks Creek
|
Rockingham
|
B25R
|
Sediment
|
69,301.00
|
LB/YR
|
4.
|
Cooks Creek
|
TMDL Development for Blacks Run and Cooks Creek
|
Rockingham
|
B25R
|
Phosphorus
|
0
|
LB/YR
|
5.
|
Muddy Creek
|
TMDL Development for Muddy Creek and Holmans Creek, Virginia
|
Rockingham
|
B22R
|
Sediment
|
286,939.00
|
LB/YR
|
6.
|
Muddy Creek
|
TMDL Development for Muddy Creek and Holmans Creek, Virginia
|
Rockingham
|
B22R
|
Phosphorus
|
38.00
|
LB/YR
|
7.
|
Holmans Creek
|
TMDL Development for Muddy Creek and Holmans Creek, Virginia
|
Rockingham/
Shenandoah
|
B45R
|
Sediment
|
78,141.00
|
LB/YR
|
8.
|
Mill Creek
|
TMDL Development for Mill Creek and Pleasant Run
|
Rockingham
|
B29R
|
Sediment
|
276.00
|
LB/YR
|
9.
|
Mill Creek
|
TMDL Development for Mill Creek and Pleasant Run
|
Rockingham
|
B29R
|
Phosphorus
|
138.00
|
LB/YR
|
10.
|
Pleasant Run
|
TMDL Development for Mill Creek and Pleasant Run
|
Rockingham
|
B27R
|
Sediment
|
0.00
|
LB/YR
|
11.
|
Pleasant Run
|
TMDL Development for Mill Creek and Pleasant Run
|
Rockingham
|
B27R
|
Phosphorus
|
0.00
|
LB/YR
|
12.
|
Linville Creek
|
Total Maximum Load Development for Linville Creek: Bacteria
and Benthic Impairments
|
Rockingham
|
B46R
|
Sediment
|
5.50
|
TONS/YR
|
13.
|
Quail Run
|
Benthic TMDL for Quail Run
|
Rockingham
|
B35R
|
Ammonia
|
7,185.00
|
KG/YR
|
14.
|
Quail Run
|
Benthic TMDL for Quail Run
|
Rockingham
|
B35R
|
Chlorine
|
27.63
|
KG/YR
|
15.
|
Shenandoah River
|
Development of Shenandoah River PCB TMDL (South Fork and
Main Stem)
|
Warren & Clarke
|
B41R B55R B57R B58R
|
PCBs
|
179.38
|
G/YR
|
16.
|
Shenandoah River
|
Development of Shenandoah River PCB TMDL (North Fork)
|
Warren & Clarke
|
B51R
|
PCBs
|
0.00
|
G/YR
|
17.
|
Shenandoah River
|
Development of Shenandoah River PCB TMDL (Main Stem)
|
Warren & Clarke
|
WV
|
PCBs
|
179.38
|
G/YR
|
18.
|
Cockran Spring
|
Benthic TMDL Reports for Six Impaired Stream Segments in the
Potomac-Shenandoah and James River Basins
|
Augusta
|
B10R
|
Organic Solids
|
1,556.00
|
LB/YR
|
19.
|
Lacey Spring
|
Benthic TMDL Reports for Six Impaired Stream Segments in the
Potomac-Shenandoah and James River Basins
|
Rockingham
|
B47R
|
Organic Solids
|
680.00
|
LB/YR
|
20.
|
Orndorff Spring
|
Benthic TMDL Reports for Six Impaired Stream Segments in the
Potomac-Shenandoah and James River Basins
|
Shenandoah
|
B52R
|
Organic Solids
|
103.00
|
LB/YR
|
21.
|
Toms Brook
|
Benthic TMDL for Toms Brook in Shenandoah County, Virginia
|
Shenandoah
|
B50R
|
Sediment
|
8.1
|
T/YR
|
22.
|
Goose Creek
|
Benthic TMDLs for the Goose Creek Watershed
|
Loudoun, Fauquier
|
A08R
|
Sediment
|
1,587
|
T/YR
|
23.
|
Little River
|
Benthic TMDLs for the Goose Creek Watershed
|
Loudoun
|
A08R
|
Sediment
|
105
|
T/YR
|
24.
|
Christians Creek
|
Fecal Bacteria and General Standard Total Maximum Daily Load
Development for Impaired Streams in the Middle River and Upper South River
Watersheds, Augusta County, VA
|
Augusta
|
B14R
|
Sediment
|
145
|
T/YR
|
25.
|
Moffett Creek
|
Fecal Bacteria and General Standard Total Maximum Daily Load
Development for Impaired Streams in the Middle River and Upper South River
Watersheds, Augusta County, VA
|
Augusta
|
B13R
|
Sediment
|
0
|
T/YR
|
26.
|
Upper Middle River
|
Fecal Bacteria and General Standard Total Maximum Daily Load
Development for Impaired Streams in the Middle River and Upper South River
Watersheds, Augusta County, VA
|
Augusta
|
B10R
|
Sediment
|
1.355
|
T/YR
|
27.
|
Mossy Creek
|
Total Maximum Daily Load Development for Mossy Creek and
Long Glade Run: Bacteria and General Standard (Benthic) Impairments
|
Rockingham
|
B19R
|
Sediment
|
0.04
|
T/YR
|
28.
|
Smith Creek
|
Total Maximum Daily Load (TMDL) Development for Smith Creek
|
Rockingham, Shenandoah
|
B47R
|
Sediment
|
353,867
|
LB/YR
|
29.
|
Abrams Creek
|
Opequon Watershed TMDLs for Benthic Impairments: Abrams
Creek and Lower Opequon Creek, Frederick and Clarke counties, Virginia
|
Frederick
|
B09R
|
Sediment
|
478
|
T/YR
|
30.
|
Lower Opequon Creek
|
Opequon Watershed TMDLs for Benthic Impairments: Abrams
Creek and Lower Opequon Creek, Frederick and Clarke counties, Virginia
|
Frederick, Clarke
|
B09R
|
Sediment
|
1,039
|
T/YR
|
31.
|
Mill Creek
|
Mill Creek Sediment TMDL for a Benthic Impairment,
Shenandoah County, Virginia
|
Shenandoah
|
B48R
|
Sediment
|
0.9
|
T/YR
|
32.
|
South Run
|
Benthic TMDL Development for South Run, Virginia
|
Fauquier
|
A19R
|
Phosphorus
|
0.038
|
T/YR
|
33.
|
Lewis Creek
|
Total Maximum Daily Load Development for Lewis Creek,
General Standard (Benthic)
|
Augusta
|
B12R
|
Sediment
|
40
|
T/YR
|
34.
|
Lewis Creek
|
Total Maximum Daily Load Development for Lewis Creek,
General Standard (Benthic)
|
Augusta
|
B12R
|
Lead
|
0
|
KG/YR
|
35.
|
Lewis Creek
|
Total Maximum Daily Load Development for Lewis Creek,
General Standard (Benthic)
|
Augusta
|
B12R
|
PAHs
|
0
|
KG/YR
|
36.
|
Bull Run
|
Total Maximum Daily Load Development for Lewis Creek, General
Standard (Benthic)
|
Loudoun, Fairfax, and Prince William counties, and the
Cities of Manassas and Manassas Park
|
A23R-01
|
Sediment
|
5,986.8
|
T/TR
|
37.
|
Popes Head Creek
|
Total Maximum Daily Load Development for Lewis Creek, General
Standard (Benthic)
|
Fairfax County and Fairfax City
|
A23R-02
|
Sediment
|
1,594.2
|
T/YR
|
38.
|
Accotink Bay
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Fairfax
|
A15R
|
PCBs
|
0.0992
|
G/YR
|
39.
|
Aquia Creek
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Stafford
|
A28E
|
PCBs
|
6.34
|
G/YR
|
40.
|
Belmont Bay/
Occoquan Bay
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Prince William
|
A25E
|
PCBs
|
0.409
|
G/YR
|
41.
|
Chopawamsic Creek
|
PCB Total Maximum Daily Load Development in the tidal Potomac
and Anacostia Rivers and their tidal tributaries
|
Prince William
|
A26E
|
PCBs
|
1.35
|
G/YR
|
42.
|
Coan River
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Northumberland
|
A34E
|
PCBs
|
0
|
G/YR
|
43.
|
Dogue Creek
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Fairfax
|
A14E
|
PCBs
|
20.2
|
G/YR
|
44.
|
Fourmile Run
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Arlington
|
A12E
|
PCBs
|
11
|
G/YR
|
45.
|
Gunston Cove
|
PCB Total Maximum Daily Load Development in the tidal Potomac
and Anacostia Rivers and their tidal tributaries
|
Fairfax
|
A15E
|
PCBs
|
0.517
|
G/YR
|
46.
|
Hooff Run & Hunting Creek
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Fairfax
|
A13E
|
PCBs
|
36.8
|
G/YR
|
47.
|
Little Hunting Creek
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Fairfax
|
A14E
|
PCBs
|
10.1
|
G/YR
|
48.
|
Monroe Creek
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Fairfax
|
A31E
|
PCBs
|
.0177
|
G/YR
|
49.
|
Neabsco Creek
|
PCB Total Maximum Daily Load Development in the tidal Potomac
and Anacostia Rivers and their tidal tributaries
|
Prince William
|
A25E
|
PCBs
|
6.63
|
G/YR
|
50.
|
Occoquan River
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Prince William
|
A25E
|
PCBs
|
2.86
|
G/YR
|
51.
|
Pohick Creek/Pohick Bay
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Fairfax
|
A16E
|
PCBs
|
13.5
|
G/YR
|
52.
|
Potomac Creek
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Stafford
|
A29E
|
PCBs
|
0.556
|
G/YR
|
53.
|
Potomac River, Fairview Beach
|
PCB Total Maximum Daily Load Development in the tidal Potomac
and Anacostia Rivers and their tidal tributaries
|
King George
|
A29E
|
PCBs
|
0.0183
|
G/YR
|
54.
|
Powells Creek
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Prince William
|
A26R
|
PCBs
|
0.0675
|
G/YR
|
55.
|
Quantico Creek
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
Prince William
|
A26R
|
PCBs
|
0.742
|
G/YR
|
56.
|
Upper Machodoc Creek
|
PCB Total Maximum Daily Load Development in the tidal
Potomac and Anacostia Rivers and their tidal tributaries
|
King George
|
A30E
|
PCBs
|
0.0883
|
G/YR
|
57.
|
Difficult Creek
|
Benthic TMDL Development for Difficult Run, Virginia
|
Fairfax
|
A11R
|
Sediment
|
3,663.2
|
T/YR
|
58.
|
Abrams Creek
|
Opequon Watershed TMDLs for Benthic Impairments
|
Frederick and Clark
|
B09R
|
Sediment
|
1039
|
T/YR
|
59.
|
Lower Opequon
|
Opequon Watershed TMDLs for Benthic Impairments
|
Frederick and Clark
|
B09R
|
Sediment
|
1039
|
T/YR
|
B. Non-TMDL waste load allocations.
Water Body
|
Permit No.
|
Facility Name
|
Outfall No.
|
Receiving Stream
|
River Mile
|
Parameter Description
|
WLA
|
Units WLA
|
VAV-B02R
|
VA0023281
|
Monterey STP
|
001
|
West Strait Creek
|
3.85
|
CBOD5
|
11.4
|
KG/D
|
VAV-B08R
|
VA0065552
|
Opequon Water Reclamation Facility
|
001
|
Opequon Creek
|
32.66
|
BOD5, JUN-NOV
|
207
|
KG/D
|
|
|
AKA Winchester - Frederick Regional
|
|
|
|
CBOD5, DEC-MAY
|
1514
|
KG/D
|
VAV-B14R
|
VA0025291
|
Fishersville Regional STP
|
001
|
Christians Creek
|
12.36
|
BOD5
|
182
|
KG/D
|
VAV-B23R
|
VA0060640
|
North River WWTF
|
001
|
North River
|
15.01
|
CBOD5, JAN-MAY
|
700
|
KG/D
|
|
7.23.04
|
AKA Harrisonburg - Rockingham Reg. Sewer Auth.
|
|
|
|
CBOD5, JUN-DEC
|
800
|
KG/D
|
TKN, JUN-DEC
|
420
|
KG/D
|
TKN, JAN-MAY
|
850
|
KG/D
|
VAV-B32R
|
VA0002160
|
INVISTA - Waynesboro Formerly Dupont - Waynesboro
|
001
|
South River
|
25.3
|
BOD5
|
272
|
KG/D
|
VAV-B32R
|
VA0025151
|
Waynesboro STP
|
001
|
South River
|
23.54
|
CBOD5
|
227
|
KG/D
|
CBOD5, JUN-OCT
|
113.6
|
KG/D
|
VAV-B32R
|
VA0028037
|
Skyline Swannanoa STP
|
001
|
South River UT
|
2.96
|
BOD5
|
8.5
|
KG/D
|
VAV-B35R
|
VA0024732
|
Massanutten Public Service STP
|
001
|
Quail Run
|
5.07
|
BOD5
|
75.7
|
KG/D
|
VAV-B37R
|
VA0002178
|
Merck & Company
|
001
|
S.F. Shenandoah River
|
88.09
|
BOD5
|
1570
|
KG/D
|
AMMONIA, AS N
|
645.9
|
KG/D
|
VAV-B49R
|
VA0028380
|
Stoney Creek Sanitary District STP
|
001
|
Stoney Creek
|
19.87
|
BOD5, JUN-NOV
|
29.5
|
KG/D
|
VAV-B53R
|
VA0020982
|
Middletown STP
|
001
|
Meadow Brook
|
2.19
|
CBOD5
|
24.0
|
KG/D
|
VAV-B58R
|
VA0020532
|
Berryville STP
|
001
|
Shenandoah River
|
24.23
|
CBOD5
|
42.6
|
KG/D
|
C. Nitrogen and phosphorus waste load allocations to restore the
Chesapeake Bay and its tidal rivers. The following table presents nitrogen and
phosphorus waste load allocations for the identified significant dischargers
and the total nitrogen and total phosphorus waste load allocations for the
listed facilities.
Virginia Waterbody ID
|
Discharger Name
|
VPDES Permit No.
|
Total Nitrogen (TN) Waste Load Allocation (lbs/yr)
|
Total Phosphorus (TP) Waste Load Allocation (lbs/yr)
|
B37R
|
Coors Brewing Company
|
VA0073245
|
54,820
|
4,112
|
B14R
|
Fishersville Regional STP
|
VA0025291
|
48,729
|
3,655
|
B32R
|
INVISTA - Waynesboro (Outfall 101)
|
VA0002160
|
78,941
|
1,009
|
B39R
|
Luray STP
|
VA0062642
|
19,492
|
1,462
|
B35R
|
Massanutten PSA STP
|
VA0024732
|
18,273
|
1,371
|
B37R
|
Merck - Stonewall WWTP (Outfall 101)
(10)
|
VA0002178
|
14,619
|
1,096
|
B12R
|
Middle River Regional STP
|
VA0064793
|
82,839
|
6,213
|
B23R
|
North River WWTF (2)
|
VA0060640
|
253,391
|
19,004
|
B22R
|
VA Poultry Growers -Hinton
|
VA0002313
|
27,410
|
1,371
|
B38R
|
Pilgrims Pride - Alma
|
VA0001961
|
18,273
|
914
|
B31R
|
Stuarts Draft WWTP
|
VA0066877
|
48,729
|
3,655
|
B32R
|
Waynesboro STP
|
VA0025151
|
48,729
|
3,655
|
B23R
|
Weyers Cave STP
|
VA0022349
|
6,091
|
457
|
B58R
|
Berryville STP
|
VA0020532
|
8,528
|
640
|
B55R
|
Front Royal STP
|
VA0062812
|
48,729
|
3,655
|
B49R
|
Georges Chicken LLC
|
VA0077402
|
31,065
|
1,553
|
B48R
|
Mt. Jackson STP (3)
|
VA0026441
|
8,528
|
640
|
B45R
|
New Market STP
|
VA0022853
|
6,091
|
457
|
B45R
|
North Fork (SIL) WWTF
|
VA0090263
|
23,390
|
1,754
|
B49R
|
Stoney Creek SD STP
|
VA0028380
|
7,309
|
548
|
B50R
|
North Fork Regional WWTP (1)
|
VA0090328
|
9,137
|
685
|
B51R
|
Strasburg STP
|
VA0020311
|
11,939
|
895
|
B50R
|
Woodstock STP
|
VA0026468
|
24,364
|
1,827
|
A06R
|
Basham Simms WWTF (4)
|
VA0022802
|
18,273
|
1,371
|
A09R
|
Broad Run WRF (5)
|
VA0091383
|
134,005
|
3,350
|
A08R
|
Leesburg WPCF
|
MD0066184
|
121,822
|
9,137
|
A06R
|
Round Hill Town WWTF
|
VA0026212
|
9,137
|
685
|
A25R
|
DSC - Section 1 WWTF (6)
|
VA0024724
|
42,029
|
2,522
|
A25R
|
DSC - Section 8 WWTF (7)
|
VA0024678
|
42,029
|
2,522
|
A25E
|
H L Mooney WWTF
|
VA0025101
|
219,280
|
13,157
|
A22R
|
UOSA - Centreville
|
VA0024988
|
1,315,682
|
16,446
|
A19R
|
Vint Hill WWTF (8)
|
VA0020460
|
8,680
|
868
|
B08R
|
Opequon WRF
|
VA0065552
|
102,336
|
7,675
|
B08R
|
Parkins Mills STP (9)
|
VA0075191
|
60,911
|
4,568
|
A13E
|
Alexandria SA WWTF
|
VA0025160
|
493,381
|
29,603
|
A12E
|
Arlington County Water PCF
|
VA0025143
|
365,467
|
21,928
|
A16R
|
Noman M Cole Jr PCF
|
VA0025364
|
612,158
|
36,729
|
A12R
|
Blue Plains (VA Share)
|
DC0021199
|
581,458
|
26,166
|
A26R
|
Quantico WWTF
|
VA0028363
|
20,101
|
1,206
|
A28R
|
Aquia WWTF
|
VA0060968
|
73,093
|
4,386
|
A31E
|
Colonial Beach STP
|
VA0026409
|
18,273
|
1,827
|
A30E
|
Dahlgren WWTF
|
VA0026514
|
9,137
|
914
|
A29E
|
Fairview Beach
|
MD0056464
|
1,827
|
183
|
A30E
|
US NSWC-Dahlgren WWTF
|
VA0021067
|
6,578
|
658
|
A31R
|
Purkins Corner STP
|
VA0070106
|
1,096
|
110
|
|
TOTALS:
|
|
5,156,169
|
246,635
|
NOTE: (1) Shenandoah Co. - North Fork Regional WWTP waste load
allocations (WLAs) based on a design flow capacity of 0.75 million gallons per
day (MGD). If plant is not certified to operate at 0.75 MGD design flow
capacity by December 31, 2010, the WLAs will be deleted and facility removed
from Significant Discharger List.
(2) Harrisonburg-Rockingham Regional S.A.-North River STP:
waste load allocations (WLAs) based on a design flow capacity of 20.8 million
gallons per day (MGD). If plant is not certified to operate at 20.8 MGD design
flow capacity by December 31, 2011, the WLAs will decrease to TN = 194,916
lbs/yr; TP = 14,619 lbs/yr, based on a design flow capacity of 16.0 MGD.
(3) Mount Jackson STP: waste load allocations (WLAs) based on
a design flow capacity of 0.7 million gallons per day (MGD). If plant is not
certified to operate at 0.7 MGD design flow capacity by December 31, 2010, the
WLAs will decrease to TN = 7,309 lbs/yr; TP = 548 lbs/yr, based on a design
flow capacity of 0.6 MGD.
(4) Purcellville-Basham Simms STP: waste load allocations
(WLAs) based on a design flow capacity of 1.5 million gallons per day (MGD). If
plant is not certified to operate at 1.5 MGD design flow capacity by December
31, 2010, the WLAs will decrease to TN = 12,182 lbs/yr; TP = 914lbs/yr, based
on a design flow capacity of 1.0 MGD.
(5) Loudoun Co. S.A.-Broad Run WRF: waste load allocations
(WLAs) based on a design flow capacity of 11.0 million gallons per day (MGD).
If plant is not certified to operate at 11.0 MGD design flow capacity by
December 31, 2010, the WLAs will decrease to TN = 121,822 lbs/yr; TP = 3,046
lbs/yr, based on a design flow capacity of 10.0 MGD.
(6) Dale Service Corp.-Section 1 WWTF: waste load allocations
(WLAs) based on a design flow capacity of 4.6 million gallons per day (MGD). If
plant is not certified to operate at 4.6 MGD design flow capacity by December
31, 2010, the WLAs will decrease to TN = 36,547 lbs/yr; TP = 2,193 lbs/yr,
based on a design flow capacity of 4.0 MGD.
(7) Dale Service Corp.-Section 8 WWTF: waste load allocations
(WLAs) based on a design flow capacity of 4.6 million gallons per day (MGD). If
plant is not certified to operate at 4.6 MGD design flow capacity by December
31, 2010, the WLAs will decrease to TN = 36,547 lbs/yr; TP = 2,193 lbs/yr,
based on a design flow capacity of 4.0 MGD.
(8) Fauquier Co. W&SA-Vint Hill STP: waste load
allocations (WLAs) based on a design flow capacity of 0.95 million gallons per
day (MGD). If plant is not certified to operate at 0.95 MGD design flow capacity
by December 31, 2011, the WLAs will decrease to TN = 5,482 lbs/yr; TP = 548
lbs/yr, based on a design flow capacity of 0.6 MGD.
(9) Parkins Mill STP: waste load allocations (WLAs) based on a
design flow capacity of 5.0 million gallons per day (MGD). If plant is not
certified to operate at 5.0 MGD design flow capacity by December 31, 2010, the
WLAs will decrease to TN = 36,547 lbs/yr; TP = 2,741 lbs/yr, based on a design
flow capacity of 3.0 MGD.
(10) Merck-Stonewall –
(a) on January 1, 2011, the following waste load allocations (WLAs)
are effective and supersede the existing WLAs: total nitrogen of 43,835 lbs/yr
and total phosphorus of 4,384 lbs/yr; (b) waste load allocations
will be reviewed and possibly reduced
based on "full-scale" results showing the optimal
treatment capability of the 4-stage Bardenpho technology at this facility
consistent with the level of effort by other dischargers in the
region. The "full scale" evaluation will be completed by December 31,
2011, and the results submitted to DEQ for review and subsequent board action;
(c) in any year when credits are available after all other exchanges within the
Shenandoah-Potomac River Basin are completed in accordance with § 62.1-44.19:18
of the Code of Virginia, Merck shall acquire credits for total nitrogen
discharged in excess of 14,619 lbs/yr and total phosphorus discharged in excess
of 1,096 lbs/yr; and (d) the allocations are not transferable and compliance
credits are only generated if discharged loads are less than the loads
identified in clause (c).
Statutory Authority
§ 62.1-44.15 of the Code of Virginia and 33 USC § 1313(e) of the
Clean Water Act.
Historical Notes
Derived from Virginia Register Volume 19, Issue 14, eff. April
24, 2003; Errata, 19:18 VA.R. 2746, 2747 May 19, 2003; amended, Virginia
Register Volume 20, Issue 24, eff. September 8, 2004; Volume 21, Issue 9, eff.
February 9, 2005; Errata, 21:11 VA.R. 1425 February 7, 2005; amended, Virginia
Register Volume 21, Issue 12, eff. March 23, 2005; Volume 22, Issue 2, eff.
November 2, 2005; Volume 22, Issue 3, eff. November 16, 2005; Volume 22, Issue
6, eff. December 28, 2005; Volume 23, Issue 11, eff. March 21, 2007; Volume 23,
Issue 15, eff. May 2, 2007; Volume 23, Issue 23, eff. October 22, 2007; Volume
24, Issue 2, eff. November 15, 2007; Volume 24, Issue 18, eff. June 11, 2008;
Volume 25, Issue 20, eff. July 8, 2009; Volume 26, Issue 6, eff. December 23,
2009; Volume 26, Issue 10, eff. February 18, 2010; Errata, 26:11 VA.R. 1859 February
1, 2010.
9VAC25-720-60. James River Basin.
A. Total maximum daily load (TMDLs).
TMDL #
|
Stream Name
|
TMDL Title
|
City/County
|
WBID
|
Pollutant
|
WLA
|
Units
|
1.
|
Pheasanty Run
|
Benthic TMDL Reports for Six Impaired Stream Segments in the
Potomac-Shenandoah and James River Basins
|
Bath
|
I14R
|
Organic Solids
|
1,231.00
|
LB/YR
|
2.
|
Wallace Mill Stream
|
Benthic TMDL Reports for Six Impaired Stream Segments in the
Potomac-Shenandoah and James River Basins
|
Augusta
|
I32R
|
Organic Solids
|
2,814.00
|
LB/YR
|
3.
|
Montebello Sp. Branch
|
Benthic TMDL Reports for Six Impaired Stream Segments in the
Potomac-Shenandoah and James River Basins
|
Nelson
|
H09R
|
Organic Solids
|
37.00
|
LB/YR
|
4.
|
Unnamed Tributary to Deep Creek
|
General Standard Total Maximum Daily Load for Unnamed
Tributary to Deep Creek
|
Nottoway
|
J11R
|
Raw Sewage
|
0
|
GAL/YR
|
5.
|
Unnamed Tributary to Chickahominy River
|
Total Maximum Daily Load (TMDL) Development for the Unnamed
Tributary to the Chickahominy River
|
Hanover
|
G05R
|
Total Phosphorus
|
409.35
|
LB/YR
|
6.
|
Rivanna River
|
Benthic TMDL Development for the Rivanna River Watershed
|
Albemarle, Greene, Nelson, and Orange
|
H27R
H28R
|
Sediment
|
10,229
|
Lbs/Day
|
B. Stream segment classifications, effluent limitations including
water quality based effluent limitations, and waste load allocations.
TABLE B1 - UPPER JAMES RIVER BASIN RECOMMENDED SEGMENT
CLASSIFICATION
|
Stream Name
|
Segment No.
|
Mile to Mile
|
Classification
|
Comments
|
Maury River
|
2-4
|
80.3-0.0
|
E.L.
|
Main & tributaries
|
James River
|
2-5
|
271.5-266.0
|
W.Q.
|
Main only
|
James River
|
2-6
|
266.0-115.0
|
E.L.
|
Main & tributaries except Tye & Rivanna River
|
Tye River
|
2-7
|
41.7-0.0
|
E.L.
|
Main & tributaries except Rutledge Creek
|
Rutledge Creek
|
2-8
|
3.0-0.0
|
W.Q.
|
Main only
|
Piney River
|
2-9
|
20.6-0.0
|
E.L.
|
Main & tributaries
|
Rivanna River
|
2-10
|
20.0-0.0
|
E.L.
|
Main & tributaries
|
Rivanna River
|
2-11
|
38.1-20.0
|
W.Q.
|
Main only
|
Rivanna River
|
2-12
|
76.7-38.1
|
E.L.
|
Main & tributaries
|
S.F. Rivanna River
|
2-13
|
12.2-0.0
|
E.L.
|
Main & tributaries
|
Mechum River
|
2-14
|
23.1-0.0
|
E.L.
|
Main & tributaries
|
N.F. Rivanna River
|
2-15
|
17.0-0.0
|
E.L.
|
Main & tributaries except Standardsville Run
|
Standardsville Run
|
2-16
|
1.2-0.0
|
W.Q.
|
Main only
|
Appomattox River
|
2-17
|
156.2-27.7
|
E.L.
|
Main & tributaries except Buffalo Creek, Courthouse
Branch, and Deep Creek
|
Buffalo Creek
|
2-18
|
20.9-0.0
|
E.L.
|
Main & tributaries except Unnamed Tributary @ R.M. 9.3
|
Unnamed Tributary of Buffalo Creek @ R.M. 9.3
|
2-19
|
1.3-0.0
|
W.Q.
|
Main only
|
Courthouse Branch
|
2-20
|
0.6-0.0
|
W.Q.
|
Main only
|
Deep Creek
|
2-21
|
29.5-0.0
|
E.L.
|
Main & tributaries except Unnamed Tributary @ R.M. 25.0
|
Unnamed Tributary of Deep Creek @ R.M. 25.0
|
2-22
|
2.2-0.0
|
W.Q.
|
Main only
|
TABLE B2 - UPPER JAMES RIVER BASIN LOAD ALLOCATIONS BASED ON
EXISTING DISCHARGE POINT7
|
Stream Name
|
Segment Number
|
Classification
|
Mile to Mile
|
Significant Discharges
|
Total Assimilative Capacity of Stream BOD5 lbs/day
|
Wasteload Allocation BOD5 lbs/day2
|
Reserve BOD5 lbs/day5
|
Cedar Creek
|
2-3
|
E.L.
|
1.9-0.0
|
Natural Bridge, Inc. STP
|
35.0
|
28.0
|
7.0 (20%)
|
Elk Creek
|
2-3
|
E.L.
|
2.8-0.0
|
Natural Bridge Camp for Boys STP
|
7.0
|
3.3
|
3.7 (53%)
|
Little Calfpasture River
|
2-4
|
E.L.
|
10.9-4.0
|
Craigsville
|
12.0
|
9.6
|
2.4 (20%)
|
Cabin River
|
2-4
|
E.L.
|
1.7-0.0
|
Millboro
|
Self -sustaining
|
None
|
None
|
Maury River
|
2-4
|
E.L.
|
19.6-12.2
|
Lexington STP
|
380.0
|
380.0
|
None
|
Maury River
|
2-4
|
E.L.
|
12.2-1.2
|
Georgia Bonded Fibers
|
760.0
|
102.03
|
238.0 (31%)
|
|
|
|
|
Buena Vista STP
|
|
420.0
|
|
Maury River
|
2-4
|
E.L.
|
1.2-0.0
|
Lees Carpets
|
790.0
|
425.03
|
290.0 (37%)
|
|
|
|
|
Glasgow STP
|
|
75.0
|
|
James River
|
2-5
|
W.Q.
|
271.5-266.0
|
Owens-Illinois
|
4,640.0
|
4,640.03
|
None
|
James River
|
2-6
|
E.L.
|
257.5-231.0
|
Lynchburg STP
|
10,100.0
|
8,000.0
|
2,060.0 (20%)
|
|
|
|
|
Babcock & Wilcox- NNFD
|
|
40.03
|
|
James River
|
2-6
|
E.L.
|
231.0-202.0
|
Virginia Fibre
|
3,500.0
|
3,500.0
|
None
|
Rutledge Creek
|
2-8
|
W.Q.
|
3.0-0.0
|
Amherst STP
|
46.0
|
37.0
|
9.0 (20%)
|
Town Creek
|
2-7
|
E.L.
|
2.1-0.0
|
Lovingston STP
|
26.0
|
21.0
|
5.0 (20%)
|
Ivy Creek
|
2-6
|
E.L.
|
0.1-0.0
|
Schuyler
|
13.8
|
11.0
|
2.8 (20%)
|
James River
|
2-6
|
E.L.
|
186.0-179.0
|
Uniroyal, Inc.
|
1,400.0
|
19.36
|
1,336.0 (95%)
|
|
|
|
|
Scottsville STP
|
|
45.0
|
|
North Creek
|
2-6
|
E.L.
|
3.1-0.0
|
Fork Union STP
|
31.0
|
25.0
|
6.0 (20%)
|
Howells Branch and Licking Hole Creek
|
2-14
|
E.L.
|
0.7-0.0
|
Morton Frozen Foods
|
20.0
|
20.03
|
None
|
Standardsville Run
|
2-16
|
W.Q.
|
1.2-0.0
|
Standardsville STP
|
17.9
|
14.3
|
3.6 (20%)
|
Rivanna River
|
2-11
|
W.Q.
|
23.5-20.0
|
Lake Monticello STP
|
480.0
|
380.0
|
100.0 (20%)
|
Rivanna River
|
2-10
|
E.L.
|
15.0-0.0
|
Palmyra
|
250.0
|
4.0
|
158.0 (63%)
|
|
|
|
|
Schwarzenbach Huber
|
|
88.03
|
|
Unnamed Tributary of Whispering Creek
|
2-6
|
E.L.
|
1.2-00
|
Dillwyn STP
|
38.0
|
30.0
|
8.0 (21%)
|
South Fork Appomattox River
|
2-17
|
E.L.
|
5.5-0.0
|
Appomattox Lagoon
|
18.8
|
15.0
|
3.8 (20%)
|
Unnamed Tributary of Buffalo Creek
|
2-19
|
W.Q.
|
1.3-0.0
|
Hampden-Sydney Coll. STP
|
10.0
|
8.0
|
2.0 (20%)
|
Appomattox River
|
2-17
|
E.L.
|
106.1-88.0
|
Farmville STP
|
280.0
|
220.0
|
60.0 (21%)
|
Unnamed Tributary of Little Guinea Creek
|
2-17
|
E.L.
|
2.5-1.3
|
Cumberland H.S. Lagoon
|
0.6
|
0.5
|
0.1 (20%)
|
Unnamed Tributary of Tear Wallet Creek
|
2-17
|
E.L.
|
0.68-0.0
|
Cumberland Courthouse
|
8.8
|
7.0
|
1.8 (20%)
|
Courthouse Branch
|
2-22
|
W.Q.
|
2.2-0.0
|
Amelia STP
|
21.0
|
17.0
|
4.0 (20%)
|
Unnamed Tributary of Deep Creek
|
2-22
|
W.Q.
|
2.2-0.0
|
Crewe STP
|
50.311,12
|
50.111, 12
|
0.2 (0.4%)11,12,13
|
1Recommended classification.
2Based on 2020 loads or stream assimilative
capacity less 20%.
3Load allocation based on published NPDES permits.
4This assimilative capacity is based upon an
ammonia loading no greater than 125.1 lbs/day.
5Percentages refer to reserve as percent of total assimilative
capacity. Minimum reserve for future growth and modeling accuracy is 20% unless
otherwise noted.
6No NPDES Permits published (BPT not established)
allocation base on maximum value monitored.
7This table is for the existing discharge point.
The recommended plan may involve relocation or elimination of stream discharge.
8Assimilative capacity will be determined upon
completion of the ongoing study by Hydroscience, Inc.
9Discharges into Karnes Creek, a tributary to the
Jackson River.
10Discharges into Wilson Creek, near its confluence
with Jackson River.
11Five-day Carbonaceous Biological Oxygen Demand
(cBOD5).
12Revision supersedes all subsequent Crewe STP
stream capacity, allocation, and reserve references.
130.4 percent reserve: determined by SWCB Piedmont
Regional Office.
Source: Wiley & Wilson, Inc.
TABLE B3 - UPPER JAMES RIVER BASIN ADDITIONAL LOAD
ALLOCATIONS
BASED ON RECOMMENDED DISCHARGE POINT
|
Stream Name
|
Segment Number
|
Classification1
|
|
Significant Discharges
|
Total Assimilative Capacity of Stream BOD5 lbs/day
|
Wasteload2 Allocation BOD5 lbs/day
|
Reserve4 BOD5 lbs/day5
|
Mill Creek
|
2-4
|
E.L.
|
5.5-0.0
|
Millboro
|
30.0
|
7.3
|
22.7 (76%)
|
Calfpasture River
|
2-4
|
E.L.
|
4.9-0.0
|
Goshen
|
65.0
|
12.0
|
53.0 (82%)
|
Maury River
|
2-4
|
E.L.
|
1.2-0.0
|
Lees Carpet
|
790.0
|
425.03
|
235.0 (30%)
|
|
|
|
|
Glasgow Regional S.T.P.
|
|
130.0
|
|
Buffalo River
|
2-7
|
E.L.
|
9.6-0.0
|
Amherst S.T.P.
|
150.0
|
120.0
|
30.0 (20%)
|
Rockfish River
|
2-6
|
E.L.
|
9.5-0.0
|
Schuyler S.T.P.
|
110.0
|
25.0
|
85.0 (77%)
|
Standardsville Run
|
|
E.L.
|
|
Standardsville
|
Land Application Recommended
|
|
South Fork Appomattox River
|
|
E.L.
|
|
Appomattox Lagoon
|
Connect to Recommended Facility in Roanoke River Basin
|
Buffalo Creek
|
2-17
|
E.L.
|
9.3-7.7
|
Hampden-Sydney College
|
46.0
|
23.0
|
23.0 (50%)
|
Unnamed trib. of Tear Wallet Creek
|
|
E.L.
|
|
Cumberland Courthouse
|
Land Application Recommended
|
|
Courthouse Branch
|
|
E.L.
|
|
Amelia
|
Land Application Recommended
|
|
Deep Creek
|
2-17
|
E.L.
|
25.0-12.8
|
Crewe S.T.P.
|
69.0
|
55.0
|
14.0 (20%)
|
1Recommended classification.
2Based on 2020 loads or stream assimilative
capacity less 20%.
3Load allocation based on published NPDES permit.
4Percentages refer to reserve as percent of total
assimilative capacity. Minimum reserve for future growth and modeling accuracy
is 20% unless otherwise noted.
5Assimilative capacity will be determined upon
completion of the ongoing study by Hydroscience, Inc.
Source: Wiley & Wilson, Inc.
TABLE B4 - SEGMENT CLASSIFICATION UPPER JAMES-JACKSON RIVER
SUBAREA
|
Stream Name
|
Segment Number
|
Mile to Mile
|
Stream Classification
|
Comments
|
Back Creek
|
2-1
|
16.06-8.46
|
W.Q.
|
Main Only
|
Jackson River
|
2-1
|
95.70-24.90
|
E.L.
|
Main and Tributaries
|
Jackson River
|
2-2
|
24.90-0.00
|
W.Q.
|
Main Only
|
Jackson River
|
2-2
|
24.90-0.00
|
E.L.
|
Tributaries Only
|
James River
|
2-3
|
349.50-308.50
|
E.L.
|
Main and Tributaries
|
James River
|
2-3
|
308.50-279.41
|
E.L.
|
Main and Tributaries
|
TABLE B5 - UPPER JAMES-JACKSON RIVER SUBAREA WASTELOAD ALLOCATIONS
BASED ON EXISTING DISCHARGE POINT1
|
MAP LOCATION
|
STREAM NAME
|
SEGMENT NUMBER
|
SEGMENT CLASSIFICATION STANDARDS
|
MILE to2 MILE
|
DISCHARGER
|
VPDES PERMIT NUMBER
|
VPDES PERMIT LIMITS BOD5 kg/day
|
303(e)3 WASTELOAD ALLOCATION BOD5
kg/day
|
1
|
Jackson River
|
2-1
|
E.L.
|
93.05-
|
Virginia Trout
|
VA0071722
|
N/A
|
Secondary
|
B
|
Warm Springs Run
|
2-1
|
E.L.
|
3.62-0.00
|
Warm Springs STP
|
VA0028233
|
9.10
|
Secondary
|
3
|
Back Creek
|
2-1
|
W.Q.
|
16.06-8.46
|
VEPCO
|
VA0053317
|
11.50
|
11.50
|
C
|
X-trib to Jackson River
|
2-1
|
E.L.
|
0.40-0.0
|
Bacova
|
VA0024091
|
9.10
|
Secondary
|
D
|
Hot Springs Run
|
2-1
|
E.L.
|
5.30-0.00
|
Hot Springs Reg. STP
|
VA0066303
|
51.10
|
Secondary
|
E
|
X-trib to Cascades Creek
|
2-1
|
E.L.
|
3.00-0.00
|
Ashwood-Healing Springs STP
|
VA0023726
|
11.30
|
Secondary
|
F
|
Jackson River
|
2-1
|
E.L.
|
50.36-
|
U.S. Forest Service Bolar Mountain
|
VA0032123
|
1.98
|
Secondary
|
G
|
Jackson River
|
2-1
|
E.L.
|
43.55
|
U.S. Army COE Morris Hill Complex
|
VA0032115
|
1.70
|
Secondary
|
H
|
Jackson River
|
2-1
|
E.L.
|
29.84-
|
Alleghany County Clearwater Park
|
VA0027955
|
5.70
|
Secondary
|
4
|
Jackson River
|
2-1
|
E.L.
|
25.99
|
Covington City Water Treatment Plant
|
VA0058491
|
N/A
|
Secondary
|
5
|
Jackson River
|
2-2
|
W.Q.
|
24.64-19.03
|
Westvaco
|
VA0003646
|
4,195.00
|
4,195.004
|
6
|
|
|
|
|
Covington City5 Asphalt Plant
|
VA0054411
|
N/A
|
N/A
|
7
|
|
|
|
|
Hercules, Inc6
|
VA0003450
|
94.00
|
94.00
|
J
|
Jackson River
|
2-2
|
W.Q.
|
19.03-10.5
|
Covington STP
|
VA0025542
|
341.00
|
341.00
|
K
|
Jackson River
|
|
|
10.5-0.0
|
Low Moor STP7
|
VA0027979
|
22.70
|
22.70
|
M
|
|
|
|
|
D.S. Lancaster CC8
|
VA0028509
|
3.60
|
3.60
|
L
|
|
|
|
|
Selma STP9
|
VA0028002
|
59.00
|
59.00
|
10
|
|
|
|
|
The Chessie System10
|
VA0003344
|
N/A
|
N/A
|
N
|
|
|
|
|
Clifton Forge STP11
|
VA0002984
|
227.00
|
227.00
|
11
|
|
|
|
|
Lydall12
|
VA0002984
|
6.00
|
6.00
|
P
|
|
|
|
|
Iron Gate STP13
|
VA0020541
|
60.00
|
60.00
|
8
|
Paint Bank Branch
|
2-2
|
E.L.
|
1.52
|
VDGIF Paint Bank Hatchery
|
VA0098432
|
N/A
|
Secondary
|
I
|
Jerrys Run
|
2-2
|
E.L.
|
6.72-
|
VDOT 1-64 Rest Area
|
VA0023159
|
0.54
|
Secondary
|
AA
|
East Branch (Sulfer Spring)
|
2-2
|
E.L.
|
2.16
|
Norman F. Nicholas
|
VA0078403
|
0.05
|
Secondary
|
BB
|
East Branch (Sulfer Spring)
|
2-2
|
E.L.
|
1.91-
|
Daryl C. Clark
|
VA0067890
|
0.068
|
Secondary
|
9
|
Smith Creek
|
2-2
|
E.L.
|
3.44-
|
Clifton Forge Water Treatment Plant
|
VA0006076
|
N/A
|
Secondary
|
O
|
Wilson Creek
|
2-2
|
E.L.
|
0.20-0.0
|
Cliftondale14 Park STP
|
VA0027987
|
24.00
|
Secondary
|
2
|
Pheasanty Run
|
2-3
|
E.L.
|
0.01-
|
Coursey Springs
|
VA0006491
|
434.90
|
Secondary
|
Q
|
Grannys Creek
|
2-3
|
E.L
|
1.20-
|
Craig Spring Conference Grounds
|
VA0027952
|
3.40
|
Secondary
|
CC
|
X-trib to Big Creek
|
2-3
|
E.L
|
1.10-
|
Homer Kelly Residence
|
VA0074926
|
0.05
|
Secondary
|
12
|
Mill Creek
|
2-3
|
E.L
|
0.16-
|
Columbia Gas Transmission Corp.
|
VA0004839
|
N/A
|
Secondary
|
R
|
John Creek
|
2-3
|
E.L
|
0.20-
|
New Castle STP(old)
|
VA0024139
|
21.00
|
Secondary
|
S
|
Craig Creek
|
2-3
|
E.L
|
48.45-36.0
|
New Castle STP (new)
|
VA0064599
|
19.90
|
Secondary
|
T
|
Craig Creek
|
2-3
|
E.L
|
46.98-
|
Craig County Schools McCleary E.S.
|
VA0027758
|
0.57
|
Secondary
|
DD
|
Eagle Rock Creek
|
2-3
|
E.L.
|
0.08-
|
Eagle Rock STP15 (Proposed)
|
VA0076350
|
2.30
|
Secondary
|
U
|
X-trib to Catawba Creek
|
2-3
|
E.L.
|
0.16
|
VDMH & R Catawba Hospital
|
VA0029475
|
13.60
|
Secondary
|
14
|
Catawba Creek
|
2-3
|
E.L.
|
23.84
|
Tarmac-Lonestar
|
VA0078393
|
0.80
|
Secondary
|
FF
|
Borden Creek
|
2-3
|
E.L
|
2.00-
|
Shenandoah Baptist Church Camp
|
VA0075451
|
0.88
|
Secondary
|
EE
|
X-trib to Borden Creek
|
2-3
|
E.L
|
0.36
|
David B. Pope
|
VA0076031
|
0.07
|
Secondary
|
V
|
X-trib to Catawba Creek
|
2-3
|
E.L
|
3.21-
|
U.S. FHA Flatwood Acres
|
VA0068233
|
0.03
|
Secondary
|
W
|
Catawba Creek
|
2-3
|
E.L
|
11.54-
|
Fincastle STP
|
VA0068233
|
8.50
|
Secondary
|
X
|
Looney Mill Creek
|
2-3
|
E.L
|
1.83-
|
VDOT I-81 Rest Area
|
VA0023141
|
0.91
|
Secondary
|
Y
|
X-trib to Stoney
|
2-3
|
E.L
|
0.57
|
VDOC Field Unit No. 25 Battle Creek
|
VA0023523
|
1.10
|
Secondary
|
Z
|
James River
|
2-3
|
E.L.
|
308.5-286.0
|
Buchanan STP
|
VA0022225
|
27.00
|
Secondary
|
TABLE B5 - NOTES:
N/A Currently No BOD5 limits or wasteload have been
imposed by the VPDES permit. Should BOD5 limits (wasteload) be
imposed a WQMP amendment would be required for water quality limited segments
only.
1Secondary treatment levels are required in
effluent limiting (E.L.) segments. In water quality limiting (W.Q.) segments
quantities listed represent wasteload allocations.
2Ending river miles have not been determined for
some Effluent Limited segments.
3These allocations represent current and original (1977
WQMP) modeling. Future revisions may be necessary based on Virginia State Water
Control Board modeling.
4The total assimilative capacity at critical stream
flow for this portion of Segment 2-2 has been modeled and verified by
Hydroscience, Inc. (March 1977) to be 4,914 kg/day BOD5.
5The discharge is to an unnamed tributary to the
Jackson River at Jackson River mile 22.93.
6The discharge is at Jackson River mile 19.22.
7The discharge is to the mouth of Karnes Creek, a
tributary to the Jackson River at Jackson River mile 5.44.
8The discharge is at Jackson River mile 6.67.
9The discharge is at Jackson River mile 5.14.
10The discharge is at Jackson River mile 4.72.
11The discharge is at Jackson River mile 3.46.
12The discharge is at Jackson River mile 1.17
13The discharge is at Jackson River mile 0.76
14The discharge is to the mouth of Wilson Creek, a
tributary to the Jackson River at Jackson River mile 2.44.
15The discharge is to the mouth of Eagle Rock
Creek, a tributary to the Jackson River at Jackson River mile 330.35.
TABLE B6 - RICHMOND CRATER INTERIM WATER QUALITY MANAGEMENT
PLAN STREAM CLASSIFICATIONS - JAMES RIVER BASIN
|
SEGMENT
|
SEGMENT NUMBER
|
MILE TO MILE
|
CLASSIFICATION
|
USGS HUC02080206 James River
|
2-19
|
115.0-60.5
|
W.Q.
|
USGS HUC02080207 Appomattox
|
2-23
|
30.1-0.0
|
W.Q.
|
TABLE B6 - *Note: A new stream segment classification for the
Upper James Basin was adopted in 1981. The SWCB will renumber or realign these segments
in the future to reflect these changes. This Plan covers only a portion of
these segments.
TABLE B7 - RICHMOND CRATER INTERIM WATER QUALITY MANAGEMENT
PLAN – CURRENT PERMITTED WASTE LOADS (March 1988)
|
|
SUMMER (June-October)
|
|
WINTER (November-May)
|
FLOW (mgd)
|
BOD5
|
NH3-N1
|
DO2 (mg/l)
|
FLOW (mgd)
|
BOD5
|
NH3-N1
|
DO2 (mg/l)
|
(lbs/d)
|
(mg/l)
|
(lbs/d)
|
(mg/l)
|
(lbs/d)
|
(mg/l)
|
(lbs/d)
|
(mg/l)
|
City of Richmond STP3
|
45.00
|
3002
|
8.0
|
-
|
-
|
-
|
|
45.00
|
5367
|
14.3
|
(lbs/d)
|
-
|
-
|
E.I. DuPont-Spruance
|
8.68
|
936
|
-
|
-
|
-
|
-
|
8.68
|
936
|
-
|
-
|
-
|
-
|
Falling Creek STP
|
9.00
|
1202
|
16.0
|
-
|
-
|
5.9
|
9.00
|
2253
|
30.0
|
-
|
-
|
5.9
|
Proctor's Creek STP
|
6.40
|
1601
|
30.0
|
-
|
-
|
5.9
|
11.80
|
2952
|
30.0
|
-
|
-
|
5.9
|
Reynolds Metals Company
|
0.39
|
138
|
-
|
7
|
-
|
-
|
0.39
|
138
|
-
|
-
|
-
|
-
|
Henrico STP
|
30.00
|
3005
|
12.0
|
-
|
-
|
5.9
|
30.00
|
7260
|
29.0
|
7
|
-
|
5.9
|
American Tobacco Company
|
1.94
|
715
|
-
|
-
|
-
|
-
|
1.94
|
716
|
-
|
-
|
-
|
-
|
ICI Americas, Inc.
|
0.20
|
152
|
-
|
-
|
-
|
-
|
0.20
|
152
|
-
|
-
|
-
|
-
|
Phillip Morris- Park 500
|
1.50
|
559
|
-
|
-
|
-
|
-
|
1.50
|
557
|
-
|
-
|
-
|
-
|
Allied (Chesterfield)
|
51.00
|
1207
|
-
|
-
|
-
|
-
|
51.00
|
1207
|
|
-
|
-
|
-
|
Allied (Hopewell)
|
150.00
|
2500
|
-
|
-
|
-
|
-
|
150.00
|
2500
|
-
|
-
|
-
|
-
|
Hopewell Regional WTF
|
34.08
|
12507
|
44.0
|
-
|
-
|
4.8
|
34.08
|
12507
|
44.0
|
-
|
-
|
4.8
|
Petersburg STP
|
15.00
|
2804
|
22.4
|
-
|
-
|
5.0
|
15.00
|
2804
|
22.4
|
-
|
-
|
5.0
|
TOTAL
|
353.19
|
30328
|
|
|
|
|
358.59
|
39349
|
|
-
|
|
|
1NH3-N values represent ammonia as
nitrogen.
2Dissolved oxygen limits represent average minimum
allowable levels.
3Richmond STP's BOD5 is permitted as
CBOD5
TABLE B7 - WASTE LOAD ALLOCATIONS FOR THE YEAR 1990
|
|
SUMMER (June-October)
|
|
WINTER (November-May)
|
FLOW (mgd)
|
CBOD5
|
NH3-N1,3
|
DO2 (mg/l)
|
CBOD5
|
NH3-N1
|
DO2 (mg/l)
|
(lbs/d)
|
(mg/l)
|
(lbs/d)
|
(mg/l)
|
(lbs/d)
|
(mg/l)
|
(lbs/d)
|
(mg/l)
|
City of Richmond STP
|
45.00
|
3002
|
8.0
|
2403
|
6.4
|
5.6
|
|
5367
|
14.3
|
5707
|
15.2
|
5.6
|
E.I. DuPont-Spruance
|
11.05
|
948
|
|
590
|
|
4.4
|
948
|
|
756
|
|
2.9
|
Falling Creek STP
|
10.10
|
1348
|
16.0
|
539
|
6.4
|
5.9
|
2023
|
24.0
|
1281
|
15.2
|
5.9
|
Proctor's Creek STP
|
12.00
|
1602
|
16.0
|
961
|
9.6
|
5.9
|
2403
|
24.0
|
1402
|
14.0
|
5.9
|
Reynolds Metals Co.
|
0.49
|
172
|
|
8
|
|
6.5
|
172
|
|
8
|
|
6.5
|
Henrico STP
|
30.00
|
3002
|
12.0
|
2403
|
9.6
|
5.6
|
4756
|
19.0
|
3504
|
44.0
|
5.6
|
American Tobacco Co.
|
2.70
|
715
|
|
113
|
|
5.8
|
715
|
|
113
|
|
5.8
|
ICI Americas, Inc.
|
0.20
|
167
|
|
8
|
|
5.8
|
167
|
|
8
|
|
3.1
|
Phillip Morris- Park 500
|
2.20
|
819
|
|
92
|
|
4.6
|
819
|
|
92
|
|
4.6
|
Allied (Chesterfield)
|
53.00
|
1255
|
|
442
|
|
5.7
|
1255
|
|
442
|
|
5.7
|
Allied (Hopewell)
|
165.00
|
2750
|
|
10326
|
|
6.1
|
2750
|
|
10326
|
|
6.1
|
Hopewell Regional WTF
|
34.07
|
12502
|
44.0
|
12091
|
36.2
|
4.8
|
12502
|
44.0
|
10291
|
36.2
|
4.8
|
Petersburg STP
|
15.00
|
2802
|
22.4
|
801
|
6.4
|
5.0
|
2802
|
22.4
|
2028
|
16.2
|
5.0
|
TOTAL
|
380.81
|
31084
|
|
28978
|
|
|
36679
|
35958
|
|
|
|
1NH3-N values represent ammonia as
nitrogen.
2Dissolved oxygen limits represent average minimum
allowable levels.
3Allied (Hopewell) allocation may be redistributed
to the Hopewell Regional WTF by VPDES permit.
TABLE B7 - WASTE LOAD ALLOCATION FOR THE YEAR 2000
|
|
SUMMER (June-October)
|
|
WINTER (November-May)
|
FLOW (mgd)
|
CBOD5
|
NH3-N1,3
|
DO2 (mg/l)
|
CBOD5
|
NH3-N1
|
DO2 (mg/l)
|
(lbs/d)
|
(mg/l)
|
(lbs/d)
|
(mg/l)
|
(lbs/d)
|
(mg/l)
|
(lbs/d)
|
(mg/l)
|
City of Richmond STP
|
45.08
|
3002
|
8.0
|
2403
|
6.4
|
5.6
|
|
5367
|
14.3
|
5707
|
15.2
|
5.6
|
E.I. DuPont-Spruance
|
196.99
|
948
|
|
590
|
|
4.4
|
948
|
|
756
|
|
2.9
|
Falling Creek STP
|
10.10
|
1348
|
16.0
|
539
|
6.4
|
5.9
|
2023
|
24.0
|
1281
|
15.2
|
5.9
|
Proctor's Creek STP
|
16.80
|
1602
|
11.4
|
961
|
6.9
|
5.9
|
2403
|
17.1
|
1402
|
10.0
|
5.9
|
Reynolds Metals Co.
|
0.78
|
172
|
|
13
|
|
6.5
|
172
|
|
13
|
|
6.5
|
Henrico STP
|
32.80
|
3002
|
11.0
|
2403
|
8.8
|
5.6
|
4756
|
17.4
|
3504
|
12.8
|
5.6
|
American Tobacco Co.
|
3.00
|
715
|
|
113
|
|
5.8
|
715
|
|
113
|
|
5.8
|
ICI Americas, Inc.
|
0.20
|
167
|
|
8
|
|
5.8
|
167
|
|
8
|
|
3.1
|
Phillip Morris- Park 500
|
2.90
|
819
|
|
92
|
|
4.6
|
819
|
|
92
|
|
4.6
|
Allied (Chesterfield)
|
56.00
|
1255
|
|
442
|
|
5.7
|
1255
|
|
442
|
|
5.7
|
Allied (Hopewell)
|
170.00
|
2750
|
|
10326
|
|
6.1
|
2750
|
|
10326
|
|
6.1
|
Hopewell Regional WTF
|
36.78
|
12502
|
40.7
|
12091
|
33.5
|
4.8
|
12502
|
40.7
|
10291
|
33.5
|
4.8
|
Petersburg STP
|
15.00
|
2802
|
22.4
|
801
|
6.4
|
5.0
|
2802
|
22.4
|
2028
|
16.2
|
5.0
|
TOTAL
|
406.43
|
31084
|
|
28982
|
|
|
36679
|
|
35963
|
|
|
1NH3-N values represent ammonia as
nitrogen.
2Dissolved oxygen limits represent average minimum
allowable levels.
3Allied (Hopewell) allocation may be redistributed
to the Hopewell Regional WTF by VPDES permit.
TABLE B7 - WASTE LOAD ALLOCATIONS FOR THE YEAR 2010
|
|
SUMMER (June-October)
|
|
WINTER (November-May)
|
FLOW (mgd)
|
CBOD5
|
NH3-N1,3
|
DO2 (mg/l)
|
CBOD5
|
NH3-N1
|
DO2 (mg/l)
|
(lbs/d)
|
(mg/l)
|
(lbs/d)
|
(mg/l)
|
(lbs/d)
|
(mg/l)
|
(lbs/d)
|
(mg/l)
|
City of Richmond STP
|
45.86
|
3002
|
7.8
|
2403
|
6.3
|
5.6
|
|
5367
|
14.0
|
5707
|
14.9
|
5.6
|
E.I. DuPont-Spruance
|
16.99
|
948
|
|
590
|
|
4.4
|
948
|
|
756
|
|
2.9
|
Falling Creek STP
|
10.10
|
1348
|
16.0
|
539
|
6.4
|
5.9
|
2023
|
24.0
|
1281
|
15.2
|
5.9
|
Proctor's Creek STP
|
24.00
|
1602
|
8.0
|
961
|
4.8
|
5.9
|
2403
|
12.0
|
1402
|
7.0
|
5.9
|
Reynolds Metals Co.
|
0.78
|
172
|
|
13
|
|
6.5
|
172
|
|
13
|
|
6.5
|
Henrico STP
|
38.07
|
3002
|
9.5
|
2403
|
7.6
|
5.6
|
4756
|
15.0
|
3504
|
11.0
|
5.6
|
American Tobacco Co.
|
3.00
|
715
|
|
113
|
|
5.8
|
715
|
|
113
|
|
5.8
|
ICI Americas, Inc.
|
0.20
|
167
|
|
8
|
|
5.8
|
167
|
|
8
|
|
3.1
|
Phillip Morris- Park 500
|
2.90
|
819
|
|
92
|
|
4.6
|
819
|
|
92
|
|
4.6
|
Allied (Chesterfield)
|
56.00
|
1255
|
|
442
|
|
5.7
|
1255
|
|
442
|
|
5.7
|
Allied (Hopewell)
|
180.00
|
2750
|
|
10326
|
|
6.1
|
2750
|
|
10326
|
|
6.1
|
Hopewell Regional WTF
|
39.61
|
12502
|
37.8
|
10291
|
31.1
|
4.8
|
12502
|
37.8
|
10291
|
31.1
|
4.8
|
Petersburg STP
|
15.00
|
2802
|
22.4
|
801
|
6.4
|
5.0
|
2802
|
22.4
|
2028
|
16.2
|
5.0
|
TOTAL
|
432.1
|
31084
|
|
28982
|
|
|
36679
|
|
35963
|
|
|
1NH3-N values represent ammonia as
nitrogen.
2Dissolved oxygen limits represent average minimum
allowable levels.
3Allied (Hopewell) allocation may be redistributed
to the Hopewell Regional WTF by VPDES permit.
C. Nitrogen and phosphorus waste load allocations to restore
the Chesapeake Bay and its tidal rivers.
The following table presents nitrogen and phosphorus waste
load allocations for the identified significant dischargers and the total
nitrogen and total phosphorus waste load allocations for the listed facilities.
Virginia Waterbody ID
|
Discharger Name
|
VPDES Permit No.
|
Total Nitrogen (TN) Waste Load Allocation (lbs/yr)
|
Total Phosphorus (TP) Waste Load Allocation (lbs/yr)
|
I37R
|
Buena Vista STP
|
VA0020991
|
41,115
|
3,426
|
I09R
|
Clifton Forge STP
|
VA0022772
|
36,547
|
3,046
|
I09R
|
Covington STP
|
VA0025542
|
54,820
|
4,568
|
H02R
|
Georgia Pacific
|
VA0003026
|
122,489
|
49,658
|
I37R
|
Lees Carpets
|
VA0004677
|
30,456
|
12,182
|
I35R
|
Lexington-Rockbridge WQCF
|
VA0088161
|
54,820
|
4,568
|
I09R
|
Low Moor STP
|
VA0027979
|
9,137
|
761
|
I09R
|
Lower Jackson River STP
|
VA0090671
|
27,410
|
2,284
|
I04R
|
MeadWestvaco
|
VA0003646
|
394,400
|
159,892
|
H12R
|
Amherst STP
|
VA0031321
|
10,964
|
914
|
H05R
|
BWX Technologies Inc.
|
VA0003697
|
187,000
|
1,523
|
H05R
|
Greif Inc.
|
VA0006408
|
73,246
|
29,694
|
H31R
|
Lake Monticello STP
|
VA0024945
|
18,182
|
1,515
|
H05R
|
Lynchburg STP (1)
|
VA0024970
|
536,019
|
33,501
|
H28R
|
Moores Creek Regional STP
|
VA0025518
|
274,100
|
22,842
|
H38R
|
Powhatan CC STP
|
VA0020699
|
8,588
|
716
|
J11R
|
Crewe WWTP
|
VA0020303
|
9,137
|
761
|
J01R
|
Farmville WWTP
|
VA0083135
|
43,856
|
3,655
|
G02E
|
R. J. Reynolds
|
VA0002780
|
25,583
|
1,919
|
G01E
|
E I du Pont - Spruance
|
VA0004669
|
201,080
|
7,816
|
G01E
|
Falling Creek WWTP
|
VA0024996
|
153,801
|
15,380
|
G01E
|
Henrico County WWTP
|
VA0063690
|
1,142,085
|
114,209
|
G03E
|
Honeywell – Hopewell
|
VA0005291
|
1,090,798
|
51,592
|
G03R
|
Hopewell WWTP
|
VA0066630
|
1,827,336
|
76,139
|
G15E
|
HRSD – Boat Harbor STP
|
VA0081256
|
740,000
|
76,139
|
G11E
|
HRSD – James River STP
|
VA0081272
|
1,250,000
|
60,911
|
G10E
|
HRSD – Williamsburg STP
|
VA0081302
|
800,000
|
68,525
|
G02E
|
Philip Morris – Park 500
|
VA0026557
|
139,724
|
2,650
|
G01E
|
Proctors Creek WWTP
|
VA0060194
|
411,151
|
41,115
|
G01E
|
Richmond WWTP (1)
|
VA0063177
|
1,096,402
|
68,525
|
G02E
|
Dominion-Chesterfield (2)
|
VA0004146
|
352,036
|
210
|
J15R
|
South Central WW Authority
|
VA0025437
|
350,239
|
35,024
|
G07R
|
Chickahominy WWTP
|
VA0088480
|
6,167
|
123
|
G05R
|
Tyson Foods – Glen Allen
|
VA0004031
|
19,552
|
409
|
G11E
|
HRSD – Nansemond STP
|
VA0081299
|
750,000
|
91,367
|
G15E
|
HRSD – Army Base STP
|
VA0081230
|
610,000
|
54,820
|
G15E
|
HRSD – VIP WWTP
|
VA0081281
|
750,000
|
121,822
|
G15E
|
JH Miles & Company
|
VA0003263
|
153,500
|
21,500
|
C07E
|
HRSD – Ches.-Elizabeth STP
|
VA0081264
|
1,100,000
|
108,674
|
|
TOTALS
|
|
14,901,739
|
1,354,375
|
NOTES: (1) Waste load allocations for localities served by combined
sewers are based on dry weather design flow capacity. During wet weather flow
events the discharge shall achieve a TN concentration of 8.0 mg/l and a TP
concentration of 1.0 mg/l.
(2) Waste load allocations are "net" loads, based on
the portion of the nutrient discharge introduced by the facility's process
waste streams, and not originating in raw water intake.
Statutory Authority
§ 62.1-44.15 of the Code of Virginia; 33 USC § 1313 of the
federal Clean Water Act.
Historical Notes
Derived from Virginia Register Volume 19, Issue 14, eff. April
24, 2003; Errata, 19:20 VA.R. 2999 June 16, 2003; amended, Virginia Register
Volume 20, Issue 24, eff. September 8, 2004; Volume 21, Issue 9, eff. February
9, 2005; Volume 21, Issue 17, eff. June 1, 2005; Volume 22, Issue 7, eff.
January 11, 2006; Errata, 22:12 VA.R. 2064 February 20, 2006; amended, Virginia
Register Volume 23, Issue 12, eff. May 21, 2007; Errata, 25:19 VA.R. 3464 May
25, 2009; amended, Virginia Register Volume 25, Issue 20, eff. July 8, 2009.
9VAC25-720-70. Rappahannock River Basin.
A. Total maximum Daily Load (TMDLs).
B. Stream segment classifications, effluent limitations
including water quality based effluent limitations, and waste load allocations.
9VAC25-720-70 Rappahannock Area Development Commission (RADCO)
208 Area Wide Waste Treatment Management Plan And Potomac-Shenandoah River
Basin 303(e) Water Quality Management Plan is included in The Potomac River
Basin section.
C. Nitrogen and phosphorus waste load allocations to restore
the Chesapeake Bay and its tidal rivers.
The following table presents nitrogen and phosphorus waste
load allocations for the identified significant dischargers and the total
nitrogen and total phosphorus waste load allocations for the listed facilities.
Virginia Waterbody ID
|
Discharger Name
|
VPDES Permit No.
|
Total Nitrogen (TN) Waste Load Allocation (lbs/yr)
|
Total Phosphorus (TP) Waste Load Allocation (lbs/yr)
|
E09R
|
Culpeper WWTP (1)
|
VA0061590
|
54,820
|
4,112
|
E02R
|
Marshall WWTP
|
VA0031763
|
7,797
|
585
|
E09R
|
Mountain Run STP (2)
|
VA0090212
|
30,456
|
2,284
|
E13R
|
Orange STP
|
VA0021385
|
36,547
|
2,741
|
E11R
|
Rapidan STP
|
VA0090948
|
7,309
|
548
|
E02R
|
Remington WWTP (3)
|
VA0076805
|
30,456
|
2,284
|
E02R
|
Clevengers Corner STP (4)
|
VA0080527
|
10,964
|
822
|
E02R
|
Warrenton Town STP
|
VA0021172
|
30,456
|
2,284
|
E18R
|
Wilderness WWTP
|
VA0083411
|
15,228
|
1,142
|
E20E
|
FMC WWTF
|
VA0068110
|
65,784
|
4,934
|
E20E
|
Fredericksburg WWTF
|
VA0025127
|
54,820
|
4,112
|
E21E
|
Haymount WWTF (5)
|
VA0089125
|
11,695
|
877
|
E24E
|
Haynesville CC WWTP
|
VA0023469
|
2,802
|
210
|
E21E
|
Hopyard Farms STP
|
VA0089338
|
6,091
|
457
|
E20E
|
Little Falls Run WWTF
|
VA0076392
|
97,458
|
7,309
|
E20E
|
Massaponax WWTF
|
VA0025658
|
97,458
|
7,309
|
E23R
|
Montross Westmoreland WWTP
|
VA0072729
|
1,584
|
119
|
E21E
|
Oakland Park STP
|
VA0086789
|
1,706
|
128
|
E23E
|
Tappahannock WWTP
|
VA0071471
|
9,746
|
731
|
E26E
|
Urbanna WWTP
|
VA0026263
|
1,218
|
91
|
E21R
|
US Army - Ft. A P Hill WWTP
|
VA0032034
|
6,457
|
484
|
E23E
|
Warsaw Aerated Lagoons
|
VA0026891
|
3,655
|
274
|
C01E
|
Omega Protein - Reedville
|
VA0003867
|
21,213
|
1,591
|
C01E
|
Reedville Sanitary District
|
VA0060712
|
2,436
|
183
|
C01E
|
Kilmarnock WTP
|
VA0020788
|
6,091
|
457
|
|
TOTALS:
|
|
614,245
|
46,068
|
NOTE: (1) Town of Culpeper WWTP waste load allocations (WLAs)
based on a design flow capacity of 4.5 million gallons per day (MGD). If plant
is not certified to operate at 4.5 MGD design flow capacity by December 31,
2010, the WLAs will decrease to TN = 36,547 lbs/yr; TP = 2,741 lbs/yr, based on
a design flow capacity of 3.0 MGD.
(2) Mountain Run STP: waste load allocations (WLAs) based on a
design flow capacity of 2.5 million gallons per day (MGD). If plant is not
certified to operate at 2.5 MGD design flow capacity by December 31, 2010, the
WLAs will decrease to TN = 18,273 lbs/yr; TP = 1,371 lbs/yr, based on a design
flow capacity of 1.5 MGD.
(3) Fauquier Co. W&SA-Remington STP: waste load
allocations (WLAs) based on a design flow capacity of 2.5 million gallons per
day (MGD). If plant is not certified to operate at 2.5 MGD design flow capacity
by December 31, 2010, the WLAs will decrease to TN = 24,364 lbs/yr; TP = 1,827
lbs/yr, based on a design flow capacity of 2.0 MGD.
(4) Clevengers Corner STP: waste load allocations (WLAs) based
on a design flow capacity of 0.9 million gallons per day (MGD). If plant is not
certified to operate at 0.9 MGD design flow capacity by December 31, 2010, the
WLAs will decrease to TN = 7,309 lbs/yr; TP = 548 lbs/yr, based on a design
flow capacity of 0.6 MGD.
(5) Haymount STP: waste load allocations (WLAs) based on a
design flow capacity of 0.96 million gallons per day (MGD). If plant is not
certified to operate at 0.96 MGD design flow capacity by December 31, 2010, the
WLAs will decrease to TN = 7,066 lbs/yr; TP = 530 lbs/yr, based on a design
flow capacity of 0.58 MGD.
Statutory Authority
§ 62.1-44.15 of the Code of Virginia; 33 USC 1313(e) of the Clean
Air Act.
Historical Notes
Derived from Virginia Register Volume 19, Issue 14, eff. April
24, 2003; amended, Virginia Register Volume 22, Issue 3, eff. November 16,
2005; Volume 23, Issue 6, eff. February 26, 2007.
9VAC25-720-80. Roanoke River Basin.
A. Total Maximum Daily Load (TMDLs).
TMDL #
|
Stream Name
|
TMDL Title
|
City/County
|
WBID
|
Pollutant
|
WLA
|
Units
|
1.
|
Ash Camp Creek
|
Total Maximum Daily Load Development for Ash Camp Creek
|
Charlotte
|
L39R
|
Sediment
|
20.7
|
T/YR
|
2.
|
North Fork Blackwater River
|
Total Maximum Daily Load (TMDL) Development for the Upper
Blackwater River Watershed
|
Franklin
|
L08R
|
Sediment
|
0
|
T/YR
|
3.
|
North Fork Blackwater River
|
Total Maximum Daily Load (TMDL) Development for the Upper
Blackwater River Watershed
|
Franklin
|
L08R
|
Phosphorus
|
0
|
T/YR
|
4.
|
Upper Blackwater River
|
Total Maximum Daily Load (TMDL) Development for the Upper
Blackwater River Watershed
|
Franklin
|
L08R
|
Sediment
|
0.526
|
T/YR
|
5.
|
Flat Creek
|
Benthic TMDL for Flat Creek Watershed, Virginia
|
Mecklenburg
|
L79R
|
Sediment
|
76.2
|
T/YR
|
6.
|
Twitty's Creek
|
Benthic TMDL for Twittys Creek Watershed, Virginia
|
Charlotte
|
L39R
|
Sediment
|
20.4
|
T/YR
|
7.
|
Roanoke River
|
Benthic TMDL Development for the Roanoke River, Virginia
|
Roanoke, Montgomery, Floyd, Botetout, Salem, Roanoke
|
L04R
|
Sediment
|
5,189
|
T/YR
|
B. Non-TMDL waste load allocations.
Water Body
|
Permit No.
|
Facility Name
|
Outfall No.
|
Receiving Stream
|
River Mile
|
Parameter Description
|
WLA
|
Units WLA
|
VAW-L04R
|
VA0072389
|
Oak Ridge Mobile Home Park
|
001
|
Falling Creek UT
|
0.32
|
BOD5
|
0.85
|
KG/D
|
VAW-L04R
|
VA0025020
|
Roanoke City Regional Water Pollution Control Plant
|
001
|
Roanoke River
|
201.81
|
BOD5
|
1173
|
KG/D
|
TKN, APR-SEP
|
318
|
KG/D
|
TKN, OCT-MAR
|
636
|
KG/D
|
|
|
|
001
|
Roanoke River
|
201.81
|
BOD5
|
1173
|
KG/D
|
TKN, APR-SEP
|
416
|
KG/D
|
TKN, OCT-MAR
|
832
|
KG/D
|
|
|
|
001
|
Roanoke River
|
201.81
|
BOD5
|
1173
|
KG/D
|
TKN, APR-SEP
|
469
|
KG/D
|
TKN, OCT-MAR
|
939
|
KG/D
|
VAW-L04R
|
VA0077895
|
Roanoke Moose Lodge
|
001
|
Mason Creek
|
7.79
|
BOD5, JUN-SEP
|
0.24
|
KG/D
|
TKN, JUN-SEP
|
0.09
|
KG/D
|
VAW-L07R
|
VA0020842
|
Bedford County School Board- Stewartsville Elementary School
|
001
|
Nat Branch, UT
|
0.59
|
BOD5
|
0.5
|
KG/D
|
VAW-L14R
|
VA0029254
|
Ferrum Water and Sewage Auth. - Ferrum Sewage Treatment
Plant
|
001
|
Storey Creek
|
9.78
|
BOD5
|
14.2
|
KG/D
|
VAW-L14R
|
VA0085952
|
Rocky Mount Town Sewage Treatment Plant
|
001
|
Pigg River
|
52
|
BOD5
|
133
|
KG/D
|
VAW-L14R
|
VA0076015
|
Ronile Incorporated
|
001
|
Pigg River
|
57.24
|
BOD5
|
14.8
|
KG/D
|
VAW-L21R
|
VA0063738
|
Bedford County School Board - Staunton River High School
|
001
|
Shoulder Run, UT
|
0.95
|
BOD5
|
1.8
|
KG/D
|
VAW-L21R
|
VA0020869
|
Bedford County School Board - Thaxton Elementary School
|
001
|
Wolf Creek, UT
|
0.35
|
BOD5
|
0.31
|
KG/D
|
VAW-L22R
|
VA0023515
|
Blue Ridge Regional Jail Auth. - Moneta Adult Detention
Facility STP
|
001
|
Mattox Creek, UT
|
3.76
|
BOD5
|
1.66
|
KG/D
|
VAW-L25R
|
VA0020851
|
Bedford County School Board - Otter River Elementary School
|
001
|
Big Otter River, UT
|
1.15
|
BOD5
|
0.4
|
KG/D
|
VAW-L26R
|
VA0022390
|
Bedford City - Sewage Treatment Plant
|
001
|
Little Otter River
|
14.36
|
BOD5
|
52.8
|
KG/D
|
VAW-L26R
|
VA0020818
|
Bedford County School Board - Body Camp Elementary
|
001
|
Wells Creek, UT
|
2.22
|
BOD5
|
0.4
|
KG/D
|
VAW-L27R
|
VA0020826
|
Bedford County School Board - New London Academy
|
001
|
Buffalo Creek, UT
|
0.67
|
BOD5
|
0.39
|
KG/D
|
VAC-L29R
|
VA0031194
|
Briarwood Village Mobile Home Park STP
|
001
|
Smith Branch, UT
|
2.82
|
BOD5
|
1.3
|
KG/D
|
VAC-L35R
|
VA0023965
|
Campbell Co Util & Serv Auth. - Rustburg
|
001
|
Mollys Creek
|
17.81
|
BOD5
|
8.13
|
KG/D
|
VAC-L39R
|
VA0084433
|
Drakes Branch WWTP
|
001
|
Twitty's Creek
|
6.04
|
BOD5
|
6.4
|
KG/D
|
VAC-L39R
|
VA0024058
|
Keysville WWTP
|
001
|
Ash Camp Creek
|
7.63
|
CBOD5, MAY-NOV
|
32.1
|
KG/D
|
TKN, MAY-NOV
|
7.57
|
KG/D
|
AC-L39R
|
VA0050822
|
Westpoint Stevens Inc Drakes Branch
|
001
|
Twittys Creek
|
7.22
|
BOD5
|
6.31
|
KG/D
|
VAW-L43R
|
VA0022985
|
Stuart Town - Sewage Treatment Plant
|
001
|
South Mayo River
|
30.78
|
BOD5
|
63.5
|
KG/D
|
VAW-L54R
|
VA0069345
|
Henry Co Public Service Auth. - Lower Smith River STP
|
001
|
Smith River
|
19.4
|
BOD5
|
257
|
KG/D
|
VAW-L54R
|
VA0025305
|
Martinsville City Sewage Treatment Plant
|
001
|
Smith River
|
22.69
|
BOD5
|
681
|
KG/D
|
VAC-L60R
|
VA0060593
|
Danville City - Northside
|
001
|
Dan River
|
53.32
|
BOD5, JUN-OCT
|
1907
|
KG/D
|
TKN, JUN-OCT
|
1817
|
KG/D
|
VAC-L66R
|
VA0020524
|
Town of Chatham STP
|
001
|
Cherrystone Creek
|
2.49
|
CBOD5
|
64.8
|
KG/D
|
TKN
|
38.9
|
KG/D
|
VAC-L75L
|
VA0020168
|
Clarksville WWTP
|
001
|
Blue Creek/John H. Kerr Reservoir
|
0.1
|
BOD5
|
59.5
|
KG/D
|
VAC-L77R
|
VA0076881
|
Chase City Regional WWTP
|
001
|
Little Bluestone Creek
|
13.67
|
CBOD5, MAY-NOV
|
29.5
|
KG/D
|
TKN, MAY-NOV
|
9.5
|
KG/D
|
VAC-L78R
|
VA0026247
|
Boydton WWTP
|
001
|
Coleman Creek
|
3.79
|
CBOD5, MAY-NOV
|
17.7
|
KG/D
|
TKN, MAY-NOV
|
4.1
|
KG/D
|
VAC-L79R
|
VA0069337
|
South Hill WWTP
|
001
|
Flat Creek
|
8.95
|
CBOD5, APR-NOV
|
60.6
|
KG/D
|
Statutory Authority
§ 62.1-44.15 of the Code of Virginia and 33 USC § 1313(e) of the
Clean Water Act.
Historical Notes
Derived from Virginia Register Volume 19, Issue 14, eff. April
24, 2003; Errata, 19:18 VA.R. 2746, 2747 May 19, 2003; amended, Virginia
Register Volume 21, Issue 9, eff. February 9, 2005; Volume 21, Issue 12, eff.
March 23, 2005; Volume 21, Issue 17, eff. June 1, 2005; Volume 22, Issue 6,
eff. December 28, 2005; Volume 23, Issue 11, eff. March 21, 2007; Volume 23,
Issue 23, eff. October 22, 2007.
9VAC25-720-90. Tennessee-Big Sandy River Basin.
A. Total Maximum Daily Load (TMDLs).
TMDL #
|
Stream Name
|
TMDL Title
|
City/County
|
WBID
|
Pollutant
|
WLA
|
Units
|
1.
|
Guest River
|
Guest River Total Maximum Load Report
|
Wise
|
P11R
|
Sediment
|
317.92
|
LB/YR
|
2.
|
Cedar Creek
|
Total Maximum Daily Load (TMDL) Development for Cedar Creek,
Hall/Byers Creek and Hutton Creek
|
Washington
|
O05R
|
Sediment
|
1,789.93
|
LB/YR
|
3.
|
Hall/Byers Creek
|
Total Maximum Daily Load (TMDL) Development for Cedar Creek,
Hall/Byers Creek and Hutton Creek
|
Washington
|
O05R
|
Sediment
|
57,533.49
|
LB/YR
|
4.
|
Hutton Creek
|
Total Maximum Daily Load (TMDL) Development for Cedar Creek,
Hall/Byers Creek and Hutton Creek
|
Washington
|
O05R
|
Sediment
|
91.32
|
LB/YR
|
5.
|
Clinch River
|
Total Maximum Daily Load Development for the Upper Clinch
River Watershed
|
Tazewell
|
P01R
|
Sediment
|
206,636
|
LB/YR
|
6.
|
Lewis Creek
|
Total Maximum Daily Load Development for the Lewis Creek
Watershed
|
Russell
|
P04R
|
Sediment
|
40,008
|
LB/YR
|
7.
|
Black Creek
|
General Standard Total Maximum Daily Load Development for Black
Creek, Wise County, Virginia
|
Wise
|
P17R
|
Manganese
|
2,127
|
KG/YR
|
8.
|
Dumps Creek
|
General Standard Total Maximum Daily Load Development for
Dumps Creek, Russell County, Virginia
|
Russell
|
P08R
|
Total Dissolved Solids
|
1,631,575
|
KG/YR
|
9.
|
Dumps Creek
|
General Standard Total Maximum Daily Load Development for
Dumps Creek, Russell County, Virginia
|
Russell
|
P08R
|
Total Suspended Solids
|
316,523
|
KG/YR
|
10.
|
Beaver Creek
|
Total Maximum Daily Load Development for the Beaver Creek
Watershed
|
Washington
|
O07R
|
Sediment
|
784,036
|
LB/YR
|
11.
|
Stock Creek
|
General Standard (Benthic) Total Maximum Daily Load
Development for Stock Creek
|
Scott
|
P13R
|
Sediment
|
0
|
T/YR
|
12.
|
Lick Creek
|
Lick Creek TMDLs for Benthic Impairments-Dickenson,
Russell and Wise Counties
|
Dickenson, Russell and Wise
|
P10R
|
Sediment
|
63
|
T/YR
|
13.
|
Cigarette Hollow
|
Lick Creek TMDLs for Benthic Impairments-Dickenson, Russell
and Wise Counties
|
Dickenson, Russell and Wise
|
P10R
|
Sediment
|
0.4
|
T/YR
|
14.
|
Laurel Branch
|
Lick Creek TMDLs for Benthic Impairments-Dickenson,
Russell and Wise Counties
|
Dickenson, Russell and Wise
|
P10R
|
Sediment
|
3.9
|
T/YR
|
15.
|
Right Fork
|
Lick Creek TMDLs for Benthic Impairments-Dickenson,
Russell and Wise Counties
|
Dickenson, Russell and Wise
|
P10R
|
Sediment
|
1.3
|
T/YR
|
B. Non-TMDL waste load allocations.
Water Body
|
Permit No.
|
Facility Name
|
Receiving Stream
|
River Mile
|
Outfall No.
|
Parameter Description
|
WLA
|
Units WLA
|
VAS-Q13R
|
VA0061913
|
Pound WWTP
|
Pound River
|
33.26
|
001
|
CBOD5, JUN-NOV
|
28
|
KG/D
|
CBOD5, DEC-MAY
|
47
|
KG/D
|
TKN, JUN-NOV
|
28
|
KG/D
|
VAS-Q14R
|
VA0026565
|
Clintwood WWTP
|
Cranes Nest River
|
9.77
|
001
|
BOD5
|
30
|
KG/D
|
VAS-O06R
|
VA0026531
|
Wolf Creek Water Reclamation Facility
|
Wolf Creek
|
7.26
|
001
|
CBOD5
|
249.8
|
KG/D
|
VAS-P01R
|
VA0026298
|
Tazewell WWTP
|
Clinch River
|
346.26
|
001
|
CBOD5, JUN-NOV
|
76
|
KG/D
|
VAS-P03R
|
VA0021199
|
Richlands Regional WWTF
|
Clinch River
|
317.45
|
001
|
BOD5, JUN-NOV
|
273
|
KG/D
|
VAS-P06R
|
VA0020745
|
Lebanon WWTP
|
Big Cedar Creek
|
5.22
|
001
|
BOD5
|
91
|
KG/D
|
VAS-P11R
|
VA0077828
|
Coeburn Norton Wise Regional WWTP
|
Guest River
|
7.56
|
001
|
CBOD5, JUN-NOV
|
303
|
KG/D
|
CBOD5, DEC-MAY
|
379
|
KG/D
|
VAS-P15R
|
VA0029564
|
Duffield Industrial Park WWTP
|
North Fork Clinch River
|
21.02
|
001
|
BOD5
|
36
|
KG/D
|
VAS-P17R
|
VA0020940
|
Big Stone Gap Regional WWTP
|
Powell River
|
177.38
|
001
|
CBOD5, JUN-NOV
|
110
|
KG/D
|
Statutory Authority
§ 62.1-44.15 of the Code of Virginia and 33 USC § 1313(e) of the
Clean Water Act.
Historical Notes
Derived from Virginia Register Volume 19, Issue 14, eff. April
24, 2003; amended, Virginia Register Volume 20, Issue 24, eff. September 8,
2004; Volume 21, Issue 9, eff. February 9, 2005; Volume 21, Issue 12, eff.
March 23, 2005; Volume 22, Issue 2, eff. November 2, 2005; Volume 22, Issue 6,
eff. December 28, 2005; Volume 23, Issue 11, eff. March 21, 2007; Volume 24,
Issue 2, eff. November 15, 2007; Volume 25, Issue 20, eff. July 8, 2009.
9VAC25-720-100. Chowan River -- Dismal Swamp River Basin.
TMDL #
|
Stream Name
|
TMDL Title
|
City/County
|
WBID
|
Pollutant
|
WLA
|
Units
|
1.
|
Unnamed Tributary to Hurricane Branch
|
Benthic TMDL for Hurricane Branch Unnamed Tributary,
Virginia
|
Nottoway
|
K16R
|
Sediment
|
60.9
|
T/YR
|
2.
|
Spring Branch
|
Total Maximum Daily Load Development for Spring Branch
|
Sussex
|
K32R
|
Phosphorus
|
145.82
|
KG/YR
|
Statutory Authority
§ 62.1-44.15 of the Code of Virginia and 33 USC § 1313(e) of the
Clean Water Act.
Historical Notes
Derived from Virginia Register Volume 21, Issue 17, eff. June
1, 2005; amended, Virginia Register Volume 23, Issue 11, eff. March 21, 2007.
9VAC25-720-110. Chesapeake Bay -- Small Coastal -- Eastern Shore
River Basin.
A. Total maximum Daily Load (TMDLs).
TMDL #
|
Stream Name
|
TMDL Title
|
City/County
|
WBID
|
Pollutant
|
WLA
|
Units
|
1.
|
Parker Creek
|
Benthic Total Maximum Daily Load (TMDL) Development for
Parker Creek, Virginia
|
Accomack
|
D03E
|
Total Phosphorus
|
664.2
|
Lbs/YR
|
B. Stream segment classifications, effluent limitations including
water quality based effluent limitations, and waste load allocations.
Small Coastal and Chesapeake Bay-
TABLE B1—CURRENT STREAM SEGMENT CLASSIFICATION
|
Segment No.
|
Name
|
Current State Class
|
7-12A
|
Pocomoke Sound
|
EL
|
7-12B
|
Messongo Creek
|
EL
|
7-12C
|
Beasley Bay
|
EL
|
7-12D
|
Chesconessex Creek
|
EL
|
7-13
|
Onancock Creek
|
WQ
|
7-14
|
Pungoteague
|
WQ
|
7-12E
|
Nandua Creek
|
EL
|
7-15
|
Occohannock Creek
|
WQ
|
7-12F
|
Nassawadox Creek
|
EL
|
7-12G
|
Hungars Creek
|
EL
|
7-12H
|
Cherrystone Inlet
|
EL
|
7-12I
|
South Bay
|
EL
|
7-12J
|
Tangier Island
|
_____
|
7-11A
|
Chincoteague
|
EL
|
7-11B
|
Hog Bogue
|
EL
|
7-11C
|
Metomkim Bay
|
EL
|
7-11D
|
Machipongo River
|
EL
|
7-11E
|
South Ocean
|
EL
|
Small Coastal and Chesapeake Bay
TABLE B2 - EASTERN SHORE WASTELOAD ALLOCATIONS
|
|
|
INTERIM WASTELOAD ALLOCATIONS(1)
|
FINAL WASTELOAD ALLOCATIONS
|
|
|
(Current Permit Limits)
|
NAME
|
RECEIVING STREAM OR ESTUARY
|
BOD5 (lb/d)
|
SUSPENDED SOLIDS (lb/d)
|
OIL & GREASE (lb/d)
|
BOD5 (lb/d)
|
SUSPENDED SOLIDS (lb/d)
|
OIL & GREASE (lb/d)
|
Commonwealth of Va. Rest Area
|
Pitts Cr.
|
4.3
|
4.3
|
--
|
4.3
|
4.3
|
--
|
Edgewood Park
|
Bullbegger Cr.
|
0.80
|
0.80
|
--
|
0.80
|
0.80
|
--
|
Holly Farms
|
Sandy Bottom Cr.
|
167(3)
|
167(3)
|
10 mg/l
|
Stream survey/model and determination of final wasteload
allocations planned for the summer of 1980.
|
Taylor Packing Company
|
Messongo Cr.
|
7006(3)
|
13010(3)
|
--
|
Stream survey/model was run previously. No change in permit
anticipated.
|
No. Accomack E.S.
|
Messongo Cr.
|
1.8
|
1.4
|
--
|
1.8
|
1.4
|
--
|
Messick & Wessels Nelsonia
|
Muddy Cr.
|
30mg/l(4)
|
30mg/l(4)
|
--
|
Interim wasteload allocations may be changed based on BAT
guidance.
|
Whispering Pines Motel
|
Deep Cr.
|
4.8
|
4.8
|
--
|
4.8
|
4.8
|
--
|
Town of Onancock
|
Onancock Cr.
|
21
|
21
|
--
|
21
|
21
|
--
|
Messick & Wessels
|
Onancock Cr.
|
30mg/l(4)
|
30mg/l(4)
|
--
|
Interim wasteload allocations may be changed based on
guidance.
|
So. Accomack E.S.
|
Pungoteague Cr.
|
1.8
|
1.4
|
--
|
1.8
|
1.4
|
--
|
A & P Exmore
|
Nassawadox Cr.
|
0.38
|
0.38
|
--
|
0.38
|
0.38
|
--
|
Norstrom Coin Laundry
|
Nassawadox Cr.
|
60mg/l(4) max.
|
60mg/l(4) max.
|
--
|
Interim wasteload allocation may be changed based on BAT
guidance.
|
NH-Acc. Memorial Hospital
|
Warehouse Cr.
|
12.5
|
12.5
|
--
|
21.5
|
12.5
|
--
|
Machipongo E.S. & H.H. Jr. High
|
Trib. To Oresbus Cr.
|
5.2
|
5.2
|
--
|
5.2
|
5.2
|
--
|
Town of Cape Charles
|
Cape Charles Harbor
|
62.6
|
62.6
|
--
|
62.6
|
62.6
|
--
|
America House
|
Chesapeake Bay
|
5
|
5
|
--
|
5
|
5
|
--
|
U.S. Coast Guard Chesapeake Bay
|
Chesapeake Bay
|
--
|
--
|
10/mgl(5)
|
--
|
--
|
10/mgl(5)
|
U.S. Government Cape Charles AFB
|
Magothy Bay
|
Currently No Discharge
|
Exmore Foods (Process Water)
|
Trib. To Parting Cr.
|
200
|
100
|
--
|
Stream survey/model and determination of final wasteload
allocations planned for the summer of 1980.
|
Exmore Foods (Sanitary)
|
Trib. To Parting Cr.
|
30mg/l(5)
|
30mg/l(5)
|
--
|
30mg/l(5)
|
30mg/l(5)
|
--
|
Perdue Foods (process water)
|
Parker Cr.
|
May-Oct
275 367
Nov-Apr.
612 797
|
--
|
--
|
Interim Permit in process. Stream survey/models were run. No
substantial change in permit anticipated.
|
Perdue Foods (parking lot)
|
Parker Cr.
|
30mg/l(5)
|
30mg/l(5)
|
--
|
30mg/l(5)
|
30mg/l(5)
|
--
|
Accomack Nursing Home
|
Parker Cr.
|
2.7
|
2.6
|
--
|
2.7
|
2.6
|
--
|
U.S. Gov't NASA Wallops Island
|
Mosquito Cr.
|
75
|
75
|
--
|
75
|
75
|
--
|
U.S. Gov't NASA Wallops Island
|
Cat Cr.
|
1.25
|
1.25
|
--
|
1.25
|
1.25
|
--
|
F & G Laundromat
|
Chincoteague Channel
|
10
|
4.8
|
--
|
Interim wasteload allocations may be changed based on BAT
guidance.
|
U.S. Coast Guard
|
Chincoteatue Channel
|
--
|
--
|
15mg/l (max.)
|
--
|
--
|
15mg/l (max.)
|
Virginia- Carolina Seafood
|
Chincoteague Bay
|
342
|
264
|
5.5
|
342
|
264
|
5.5
|
Reginald Stubbs Seafood Co. (VA0005813)
|
Assateague Channel
|
--
|
20
|
95
|
--
|
20
|
95
|
Reginald Stubbs Seafood Co. (VA00056421)
|
Assateague Channel
|
--
|
20
|
98
|
--
|
20.4(2)
|
98
|
Shreaves
|
Chincoteague Bay
|
--
|
16(2)
|
1.4(2)
|
--
|
16(2)
|
1.4(2)
|
Chincoteague Seafood
|
Chincoteague Bay
|
342
|
264
|
5.5
|
342
|
264
|
5.5
|
TABLE B3 - EXISTING OR POTENTIAL SOURCES OF WATER POLLUTION
|
Location No.
|
Name
|
Receiving Estuary
|
Stream
|
Flow (MGD)
|
CBOD (mgl/#D)
|
NBOD (mgl/#D)
|
Total Suspended Solids (mgl/#D)
|
D.O. (mgl)
|
FC (MPN/ 100ml)
|
Treatment/ Operation
|
1
|
Comm. Va. Rest Area
|
Pocomoke Sound
|
Pitts Cr.
|
.003
|
7/0.18
|
|
10/0.3
|
7.5
|
1
|
Extended aeration. Sec. Holding pond, CL2
|
2
|
H.E. Kelley
|
Pocomoke Sound
|
Pitts Cr.
|
|
|
|
|
|
|
Currently no discharges. Out of business
|
3
|
Edgewood Park
|
Pocomoke Sound
|
Bullbegger Creek
|
.006(3)
|
16/0.8(2)
|
|
16/0.8(2)
|
|
|
PRI, CL2. Holding Pond
|
4
|
Holly Farms
|
Pocomoke Sound
|
Sand Bottom Creek
|
0.18
|
6/40
|
|
15/100
|
8.0
|
100
|
Aerated Lagoons, CL2
|
5
|
J.W. Taylor
|
Messongo Creek
|
Trib. To Messongo
|
.001
|
60/50
|
|
150/125
|
8.0
|
|
Aerated Lagoons
|
6
|
No. Accomack E.S.
|
Messongo Creek
|
Trib. To Messongo
|
.005
|
22/0.9
|
|
30/1.3
|
9.0
|
|
Sec., Septic Tank, Sand Filter Holding Pond
|
7
|
Messick & Wessells-Nelsonia
|
Beasly Bay
|
Muddy Creek
|
.005
|
125/5.2
|
|
100/4.2
|
|
|
Sec., Extended Aeration
|
8
|
Willets Laundromat
|
Beasly Bay
|
Hunting Creek
|
|
|
|
|
|
|
Prl., Septic Tank
|
9
|
Byrd Food
|
Beasly Bay
|
|
|
|
|
|
|
|
No discharge industry
|
10
|
Whispering Pines Motel
|
Beasly Bay
|
Deep Creek
|
.009
|
25/1.9
|
|
30/2.3
|
6.0
|
|
Sec., Extended Aeration Holding Pond, CL2
|
11
|
Town of Onancock
|
Onancock Creek
|
North Fork
|
.19
|
2/3.2
|
|
3/4.8
|
7.5
|
3
|
Primary, Primary Settling Sludge Digestion, CL2
|
12
|
Messick & Wessels-Onley
|
Onancock Creek
|
Joynes Branch
|
.005
|
100/4.2
|
|
150/6.3
|
|
|
Sec., Extended Aeration
|
13
|
So. Accomack E.S.
|
Pungoteague
|
Trib. To Pungoteague
|
|
24/1.8(2)
|
|
19/1.4(2)
|
|
|
Sec., Septic Tank, Grease Trap, Sand Filter, Holding Pond.
No discharge in 4 yrs.
|
14
|
Great Atlantic & Pacific Tea Company
|
Nassawadox
|
Nassawadox
|
.001
|
140/1.2
|
|
150/1.3
|
|
6.5
|
Sec., Extended Aeration CL2
|
15
|
Norstrom Coin Laundry
|
Nassawadox
|
Trib. To Nassawadox
|
.008
|
|
|
|
|
|
Sec., Extended Aeration, permit in process
|
17
|
N.H.-Acc. Memorial Hospital
|
Nassawadox
|
Warehouse Creek
|
.03
|
25/1.6
|
|
35/2.2
|
6.5
|
750
|
Secondary Aerated Lagoon, CL2 Holding pond
Stab-Lagoon
|
18
|
Machipongo E.S. & N.H. Jr. High School
|
Hungars Creek
|
Trib. To Oresbus
|
0.3(1)
|
30/5.2(2)
|
|
30/5.2(2)
|
|
|
Sec., Stab-Lagoon, Holding Pond no discharge in 4 yrs.
|
19
|
B & B Laundromat
|
Cherry Stone Inlet
|
Old Castle Creek
|
|
|
|
|
|
|
Prl. Septic Tank w/discharger
|
20
|
KMC Foods, Inc.
|
Cherry Stone Inlet
|
|
|
|
|
|
|
|
No-Discharge industry
|
21
|
Herbert West Laundromat
|
Cherry Stone Inlet
|
Kings Creek
|
|
|
|
|
|
|
Prl. Septic Tank w/Discharger
|
22
|
Town of Cape Charles
|
Cape Charles Harbor
|
Cape Charles Harbor
|
.165(2)
|
290/400(3)
|
|
139/192(3)
|
|
|
Raw Sewage, Sewage Treatment to be completed by 1982
|
23
|
American House Inn
|
Chesapeake Bay
|
Chesapeake Bay
|
|
30/5(2)
|
|
30/5(2)
|
|
|
|
24
|
U.S. Coast Guard
|
Chesapeake Bay
|
Chesapeake Bay
|
.001(2)
|
30/
|
|
|
5.0(2)
|
200(2)
|
Bilgewater
|
25
|
U.S. Gov't Cape Charles AFS
|
Magothy
|
Magothy
|
.001(2)
|
|
|
|
5.0(3)
|
|
Sec., CL2, Aerated Lagoon, currently no-discharge
|
27
|
Exmore Frozen Foods
|
Machipongo
|
Trib. To Parting Cr.
|
.56
|
29/135
|
|
18/84
|
6.5
|
|
Grass Bays, Screening
|
28
|
Exmore Foods (Domestic)
|
Machipongo
|
Trib. To Parting Cr.
|
.02
|
5/0.8
|
|
9/1.5
|
|
|
Septic Tank, Sand Filter
|
30
|
Perdue Foods
|
Metomkin Bay
|
Parker Creek
|
1.7
|
11/156
|
|
15/213
|
6.5
|
150
|
Sec., Aerated Lagoon, Holding Pond, CL2
|
31
|
Perdue Foods
|
Metomkin Bay
|
Parker Cr.
|
.01(4)
|
|
|
15/1.3
|
|
|
|
32
|
Accomack Co. Nursing Home
|
Metomkin Bay
|
Parker Cr. North Fork
|
.011
|
20/1.8
|
|
28/2.6
|
6.5
|
100
|
Sec., Extended Aeration, Holding Pond, CL2
|
33
|
U.S. Gov't NASA (Wallops Island)
|
Hog Creek
|
Cat Creek
|
.005
|
30/
|
|
30/
|
|
|
Sec., Stab., Pond, Holding Pond, CL2
|
34
|
Robo Automatic Car
|
Chincoteague Channel
|
Little Simoneaton
|
|
|
|
|
|
|
|
35
|
U.S. Gov't NASA
|
Chincoteague Channel
|
Mosquito Creek
|
.105
|
10.6/9.3(3)
|
112/28
|
2.0/1.8
|
|
|
Sec., Trickling Filter
|
36
|
Trail's End Rec. Vehicle Dev.
|
Chincoteague Channel
|
Trib to Mosquito Cr.
|
|
|
|
|
|
|
Septic Tank and Drainfield
|
37
|
Coin-Op Laundromat
|
Chincoteague Channel
|
Chincoteague Channel
|
|
|
|
|
|
|
No discharge
|
38
|
F & G Laundromat
|
Chincoteague Channel
|
Chincoteague Channel
|
.005
|
|
|
|
|
|
|
39
|
U.S. Coast Guard
|
Chincoteague Channel
|
Chincoteague Channel
|
.001(2)
|
|
|
30/0.2(2)
|
|
200(2)
|
Discharge-Bilgewater
|
40
|
Phillip Custis
|
Ramshorn Bay
|
|
|
|
|
|
|
|
Spray Irrigation, no Discharge
|
43
|
Boggs (Melfa)
|
Nickowampus Creek
|
|
|
|
|
|
|
|
Septic tank waste lagoons, no discharge
|
44
|
Blake (Greenbush)
|
Deep Creek
|
|
|
|
|
|
|
|
Septic tank waste lagoon, no discharge
|
45
|
Cherrystone Campground
|
Kings Creek or Cherrystone Inlet
|
|
|
|
|
|
|
|
Stab-Lagoon, Holding pond, no discharge
|
46
|
Wallops Sanitary Landfill
|
|
|
|
|
|
|
|
|
Solid waste disposal site, no discharge
|
47
|
Chincoteague Dumpsite
|
|
|
|
|
|
|
|
|
Solid waste disposal site, no discharge
|
48
|
Bob Town Sanitary Landfill
|
|
|
|
|
|
|
|
|
Solid waste disposal site, no discharge
|
49
|
Northampton Sanitary Landfill
|
|
|
|
|
|
|
|
|
Solid waste site, no discharge
|
52
|
Dorsey's Seafood Market
|
Chincoteague
|
|
|
|
|
|
|
|
Oysters(5)
|
54
|
Va-Carolina Seafood Company, Inc.
|
Hog-Bogue
|
|
|
|
|
1152(2) Clams
|
|
|
Surf Clams, Oysters, Scallops
|
68(2) Oysters
|
7.0(2) Scallops
|
55
|
Chincoteague Island Oyster Farm
|
Chincoteague
|
|
|
|
|
|
|
|
(Oyster-Boat Operation (grows oysters & clams from
larvae)(6)
|
|
Reginald Stubbs Seafood Company
|
Assateague Channel
|
|
.002(4)
|
4.2
|
|
2.8
|
|
|
Oyster
|
58
|
Shreaves Bros.
|
Chincoteague
|
|
.002(4)
|
2.07
|
|
8.0
|
|
|
Oyster
|
60
|
Chincoteague Seafood Co.
|
Chincoteague
|
|
.063(4)
|
972
|
|
79.9
|
|
|
Surf-Clam
|
61
|
Ralph E. Watson Oyster Co.
|
Chincoteague
|
|
.003(4)
|
57
|
|
53
|
|
|
Oyster
|
62
|
McCready Bros. Inc.
|
Chincoteague
|
|
|
|
|
|
|
|
Oyster, no discharge
|
63
|
Wm. C. Bunting
|
Chincoteague
|
|
.001(4)
|
12
|
|
4.8
|
|
|
Oyster
|
64
|
Carpenters Seafood
|
Chincoteague
|
|
.001(4)
|
4.1
|
|
2.1
|
|
|
Oyster
|
64a
|
Burtons Seafood, Inc.
|
Chincoteague
|
|
.006(4)
|
10.3
|
|
.35
|
|
|
Oyster shell stock deal no discharge
|
69
|
Jones Bros. Seafood
|
Chincoteague
|
Sheepshead Cr.
|
|
|
|
|
|
|
Oyster & Clams
|
70
|
W.E. Jones Seafood
|
Chincoteague
|
Sheepshead Creek
|
|
|
|
46.4(2)
|
|
|
Oyster & Clams
|
71
|
Conner & McGee Seafood
|
Chincoteague
|
Sheepshead Creek
|
|
|
|
|
|
|
Oyster & Clams(6)
|
72
|
Hills Oyster Farm
|
Chincoteague
|
|
|
|
|
|
|
|
Oyster & Clams(5)
|
73
|
Thomas E. Reed Seafood
|
Chincoteague
|
Deep Hole Creek
|
|
|
|
|
|
|
Oyster & Clams(6)
|
74
|
Mears & Powell
|
Metomkin
|
|
|
|
|
|
|
|
Oyster-Building, also used to clean fish(5)
|
75
|
Wachapreague Seafood Company
|
Metomkin
|
Finney Creek
|
.036(4)
|
|
|
144
|
|
|
Sea Clam
|
76
|
George D. Spence and Son
|
Machipongo
|
|
|
|
|
|
|
|
Crab Shedding(6)
|
77
|
George D. Spence and Son
|
Machipongo
|
|
|
|
|
|
|
|
Crab Picking, no discharge
|
78
|
George T. Bell
|
Machipongo
|
|
|
|
|
|
|
|
No Discharge, Oyster
|
79
|
George D. Spence and Son
|
Machipongo
|
Upshur Bay
|
|
|
|
|
|
|
Oyster(6)
|
80
|
Peters Seafood
|
Machipongo
|
|
|
|
|
|
|
|
Oyster(6)
|
81
|
J.E. Hamblin
|
Machipongo
|
|
|
|
|
|
|
|
Oyster, No discharge
|
83
|
Nathan Bell Seafood
|
Machipongo
|
|
|
|
|
|
|
|
Clams, Hard(5)
|
84
|
John L. Marshall Seafood
|
Machipongo
|
|
|
|
|
|
|
|
Clams(5)
|
85
|
American Original Foods, Inc.
|
Machipongo
|
Parting Creek
|
.151(4)
|
2632
|
|
1337
|
|
|
|
86
|
Harvey & Robert Bowen
|
Machipongo
|
Parting Creek
|
.0006(4)
|
6.2
|
|
1.7
|
|
|
Oyster
|
87
|
H.M. Terry
|
Machipongo
|
Parting Creek
|
.0004(4)
|
3.3
|
|
.62
|
|
|
Oyster
|
89
|
Webb's Island Seafood
|
South Ocean Area
|
|
|
|
|
|
|
|
Clams(6)
|
90
|
Cliff's Seafood
|
South Ocean Area
|
Mockhorn Bay
|
|
|
|
|
|
|
Oyster & Clam(6)
|
92
|
H. Allen Smith
|
South Ocean Area
|
|
.037(4)
|
213
|
|
522
|
|
|
Sea Clam
|
94
|
C & D Seafood, Inc.
|
South Ocean Area
|
Oyster Harbor
|
.04(4)
|
427
|
|
204 sea clam
|
|
|
Sea Clam, Oyster
|
34(2) oyster
|
95
|
B.L. Bell & Sons
|
South Ocean Area
|
Oyster Harbor
|
.001(4)
|
12
|
|
.9
|
|
|
Oyster
|
98
|
Lance Fisher Seafood Co.
|
Pocomoke
|
|
.02(4)
|
38
|
|
12.8
|
|
|
Oyster and Clam
|
99
|
Fisher & Williams/Lester Fisher
|
Messongo
|
|
|
|
|
|
|
|
Building used to shed soft crabs(5)
|
100
|
Grady Rhodes Seafood
|
Messongo
|
|
|
|
|
|
|
|
Sold business, Building used to shed soft crabs(5)
|
101
|
Bonowell Bros.
|
Messongo
|
Pocomoke Sound
|
.001(4)
|
12
|
|
2.5
|
|
|
Oyster
|
102
|
John H. Lewis & Co.
|
Messongo
|
Starling Creek
|
|
|
|
|
|
|
Oyster SS only, no discharge
|
103
|
Eastern Shore Seafood
|
Beasly
|
|
|
|
|
|
|
|
Crab, no discharge
|
106
|
Ashton's Seafood, Inc.
|
Pungoteague
|
|
|
|
|
|
|
|
Shell stock dealer-no discharge
|
107
|
Nandua Seafood Co.
|
Nandua
|
|
.0001(4)
|
.2
|
|
.9
|
|
|
Crab
|
108
|
A.M. Acuff
|
Cherrystone
|
|
|
|
|
|
|
|
Building used for storage, no discharge
|
110
|
D.L. Edgerton Co.
|
Cherrystone
|
Mud Creek
|
|
|
|
|
|
|
Conch. In operation. Retort drains overboard & fish
wash-down(6)
|
111 & 112
|
Tangier Island Seafood, Inc.
|
Tangier
|
|
|
|
|
|
|
|
Crab(5)
|
113
|
Tangier
|
Chesapeake Bay
|
|
|
|
|
|
|
|
1000 KW Power Station
|
114
|
Chincoteague
|
Chincoteague Channel
|
|
|
|
|
|
|
|
2100 KW Power Station
|
115
|
Parksley
|
|
|
|
|
|
|
|
|
2400 KW Power Station
|
116
|
Tasley
|
|
|
|
|
|
|
|
|
1400 KW Power Station
|
117
|
Bayview
|
|
|
|
|
|
|
|
|
10,000 KW Power Station
|
118
|
Cape Charles
|
Cape Charles Harbor
|
|
|
|
|
|
|
|
1200 KW Power Station
|
119
|
Burdick Well & Pump Company
|
|
|
|
|
|
|
|
|
Holding Pond, no discharge
|
120
|
Marshall & Son Crab Company
|
Messongo Cr.
|
|
|
|
|
|
|
|
Crab Shedding(6)
|
|
Linton & Lewis Crab Co.
|
Pocomoke Sound
|
|
|
|
|
|
|
|
Crab Shedding(6)
|
122
|
D.L. Edgerton
|
Chincoteague
|
|
|
|
|
|
|
|
Fish Washdown(6)
|
123
|
Evans Bros. Seafood Co.
|
Pocomoke Sound
|
|
|
|
|
|
|
|
Crab Shedding(6)
|
124
|
Stanley F. Linton
|
Messongo
|
Starling Cr.
|
|
|
|
|
|
|
Crab Shedding(6)
|
125
|
H.V. Drewer & Son
|
Messongo
|
Starling Cr.
|
.035(4)
|
349
|
|
736-clam
|
|
|
Oyster & Clam
|
.018(4)
|
180
|
198-oyster
|
126
|
Chincoteague Fish Co., Inc.
|
Chincoteague Channel
|
|
|
|
|
|
|
|
Fish Washdown(6)
|
127
|
Chincoteague Crab Company
|
Assateague Channel
|
|
|
.18(2)
|
|
.54(2)
|
|
|
Crab & Crab Shedding
|
128
|
Aldon Miles & Sons
|
Pocomoke Sound
|
|
|
|
|
|
|
|
Crab Shedding(6)
|
129
|
Saxis Crab Co.
|
Messongo
|
Starling Cr.
|
|
|
|
|
|
|
Crab Shedding(6)
|
|
Paul Watkinson SFD
|
Pocomoke Sound
|
|
|
|
|
|
|
|
Crab Shedding(6)
|
131
|
Russell Fish Co., Inc
|
Chincoteague Channel
|
|
|
|
|
|
|
|
Fish(6)
|
132
|
Mason Seafood Co.
|
Chincoteague Channel
|
|
.002(4)
|
7.7
|
|
13.7
|
|
|
Oysters
|
NOTE: (1)Water quality data taken from Discharge
Monitoring Reports or special studies unless indicated.
(2)NPDES Permit limits given since the permit is
new and discharge monitoring reports not yet available.
(3)Data from Accomack-Northampton Co. Water Quality
Management Plan.
(4)Estimated.
(5)May need a permit--either company has not
responded to SWCB letter or operation has just started up.
(6)No limits -- has an NPDES permit, but is not
required to monitor.
C. Nitrogen and phosphorus waste load allocations to restore
the Chesapeake Bay and its tidal rivers. The following table presents nitrogen
and phosphorus waste load allocations for the identified significant
dischargers and the total nitrogen and total phosphorus waste load allocations
for the listed facilities.
Virginia Waterbody ID
|
Discharger Name
|
VPDES Permit No.
|
Total Nitrogen (TN) Waste Load Allocation (lbs/yr)
|
Total Phosphorus (TP) Waste Load Allocation (lbs/yr)
|
C16E
|
Cape Charles Town WWTP (1)
|
VA0021288
|
6,091
|
457
|
C11E
|
Onancock WWTP (2)
|
VA0021253
|
9,137
|
685
|
C13E
|
Shore Memorial Hospital
|
VA0027537
|
1,218
|
91
|
C10E
|
Tangier WWTP
|
VA0067423
|
1,218
|
91
|
C10R
|
Tyson Foods – Temperanceville
|
VA0004049
|
22,842
|
1,142
|
|
TOTALS:
|
|
40,506
|
2,467
|
NOTE: (1) Cape Charles STP: waste load allocations (WLAs)
based on a design flow capacity of 0.5 million gallons per day (MGD). If plant is
not certified to operate at 0.5 MGD design flow capacity by December 31, 2010,
the WLAs will decrease to TN = 3,046 lbs/yr; TP = 228 lbs/yr, based on a design
flow capacity of 0.25 MGD.
(2) Onancock STP: waste load allocations (WLAs) based on a
design flow capacity of 0.75 million gallons per day (MGD). If plant is not
certified to operate at 0.75 MGD design flow capacity by December 31,
2011, the WLAs will decrease to TN = 3,046 lbs/yr; TP = 228 lbs/yr,
based on a design flow capacity of 0.25 MGD.
Statutory Authority
§ 62.1-44.15 of the Code of Virginia; 33 USC § 1313(e) of the
Clean Water Act.
Historical Notes
Derived from Virginia Register Volume 19, Issue 14, eff. April
24, 2003; amended, Virginia Register Volume 22, Issue 3, eff. November 16,
2005; Volume 22, Issue 16, eff. May 17, 2006; Volume 25, Issue 20, eff. July 8,
2009; Volume 26, Issue 6, eff. December 23, 2009.
9VAC25-720-120. York River Basin.
A. Total Maximum Daily Load (TMDLs).
B. Stream segment classifications, effluent limitations
including water quality based effluent limitations, and waste load allocations.
TABLE B1 -- RECOMMENDED STREAM SEGMENTS IN THE YORK RIVER
BASIN
|
Segment Number
|
Classification
|
Name of River (Description)*
|
8-1
|
EL
|
North Anna River (main and tributaries except Goldmine Creek
and Contrary Creek) R.M. 68.4-0.0
|
8-2
|
EL
|
Goldmine Creek
|
8-3
|
WQ
|
Contrary Creek (main only) R.M. 9.5-0.0
|
8-4
|
EL
|
South Anna River (main and tributaries) R.M. 101.2-97.1
|
8-5
|
EL
|
South Anna River (main only) R.M. 97.1-77.4
|
8-6
|
EL
|
South Anna River (main and tributaries) R.M.77.4-0.0
|
8-7
|
EL
|
Pamunkey River (main and tributaries) R.M. 90.7-12.2
|
8-8
|
WQ
|
Pamunkey River (main only) R.M. 12.2-0.0
|
8-9
|
EL
|
Mattaponi River (main and tributaries) R.M.102.2-10.2
|
8-10
|
EL
|
Mattaponi River (main only) R.M.10.2-0.0
|
8-11
|
WQ
|
York River (main only) R.M. 30.4-22.4
|
8-12
|
EL
|
York River (main and tributaries except King Creek and
Carter Creek) –R.M. 22.4-0.0
|
8-13
|
EL
|
Carter Creek (main and tributaries) R.M. 5.4-2.0
|
8-14
|
EL
|
Carter Creek (main only) R.M. 2.0-0.0
|
8-15
|
EL
|
King Creek (main only) R.M.5.6-0.0
|
8-16
|
WQ
|
Condemned shellfish areas- Timberneck, Queens, and Sarah Creeks
and portions of the main stream of the York River.
|
*R.M.= River Mile, measured from the river mouth
|
Source: Roy F. Western
TABLE B2 -- WASTE LOAD ALLOCATIONS (IN LBS PER DAY)
|
POINT SOURCE
|
1977 WASTE LOAD2
|
MAXIMUM7 DAILY LOAD
|
RECOMMENDED ALLOCATION
|
RAW WASTE LOAD AT 1995
|
REQUIRED & REMOVAL EFFICENCY 1995
|
CBOD5
|
UBOD1
|
CBOD5
|
UBOD
|
CBOD5
|
UBOD
|
PERCENT
RESERVE
|
CBOD5
|
UBOD
|
CBOD5
|
UBOD
|
Gordonsville
|
145
|
398
|
150
|
412
|
150
|
412
|
0
|
1950
|
2730
|
92
|
85
|
Louisa-Mineral
|
50
|
108
|
55
|
118
|
55
|
118
|
0
|
850
|
1150
|
93
|
90
|
Doswell
|
52
|
110
|
8628
|
14078
|
6908
|
11258
|
20
|
1080
|
1444
|
854
|
71
|
Thornburg
|
63
|
150
|
68
|
162
|
68
|
162
|
0
|
1240
|
1690
|
94
|
90
|
Bowling Green
|
27
|
64
|
29
|
68
|
29
|
68
|
0
|
680
|
926
|
96
|
93
|
Ashland
|
160
|
303
|
235
|
559
|
188
|
447
|
20
|
2250
|
3825
|
92
|
88
|
Hanover (Regional STP)
|
170
|
437
|
280
|
820
|
280
|
820
|
0
|
5730
|
7930
|
96
|
90
|
Chesapeake Corp.
|
6400
|
8000
|
104455
|
150005
|
104455
|
150005
|
N/A
|
51700
|
64630
|
90
|
90
|
West Point
|
105
|
380
|
2813
|
1020
|
225
|
814
|
20
|
1000
|
1600
|
854
|
66
|
1BOD is Ultimate Biochemical Oxygen Demand. Its concentration
is derived by the following: BOD5 /0.80+ 4.5(TKN)=(UBOD). NOTE:
The amount of TKN utilized depends on the location in the basin.
2Projected for 1977 based on population
projections.
3Recommended allocation based on BPCTCA effluent
guidelines applied to raw waste loads at 2020.
4Minimum removal efficiency.
5Allocation based on BPCTCA effluent guidelines;
amended by Minute 25, June 3-5, 1979 board meeting.
7Assimilative capacity.
8Amended by Minute 1, August 17, 1978, board
meeting.
|
Source: Roy F. Weston, Inc.
C. Nitrogen and phosphorus waste load allocations to restore
the Chesapeake Bay and its tidal rivers. The following table presents nitrogen
and phosphorus waste load allocations for the identified significant
dischargers and the total nitrogen and total phosphorus waste load allocations
for the listed facilities.
Virginia Waterbody ID
|
Discharger Name
|
VPDES Permit No.
|
Total Nitrogen (TN) Waste Load Allocation (lbs/yr)
|
Total Phosphorus (TP) Waste Load Allocation (lbs/yr)
|
F20R
|
Caroline County STP
|
VA0073504
|
9,137
|
1,066
|
F01R
|
Gordonsville STP
|
VA0021105
|
17,177
|
2,004
|
F04R
|
Ashland WWTP
|
VA0024899
|
36,547
|
4,264
|
F09R
|
Doswell WWTP
|
VA0029521
|
18,273
|
2,132
|
F09R
|
Bear Island Paper Company
|
VA0029521
|
47,328
|
12,791
|
F27E
|
Giant Yorktown Refinery
|
VA0003018
|
167,128
|
22,111
|
F27E
|
HRSD - York River STP
|
VA0081311
|
274,100
|
31,978
|
F14R
|
Parham Landing WWTP(1)
|
VA0088331
|
36,547
|
4,264
|
F14E
|
Smurfit Stone - West Point
|
VA0003115
|
259,177
|
70,048
|
F12E
|
Totopotomoy WWTP
|
VA0089915
|
182,734
|
21,319
|
F25E
|
West Point STP
|
VA0075434
|
10,964
|
1,279
|
C04E
|
HRSD - Mathews Courthouse STP
|
VA0028819
|
1,827
|
213
|
|
TOTALS:
|
|
1,060,939
|
173,469
|
NOTES: (1) Parham Landing WWTP: waste load
allocations (WLAs) based on a design flow capacity of 2.0 million gallons per
day (MGD). If plant is not certified to operate at 2.0 MGD design flow capacity
by December 31, 2010, the WLAs will decrease to TN = 10,416 lbs/yr; TP = 1,215
lbs/yr, based on a design flow capacity of 0.57 MGD.
Statutory Authority
§ 62.1-44.15 of the Code of Virginia; 33 USC § 1313(e) of
the Clean Water Act.
Historical Notes
Derived from Virginia Register Volume 19, Issue 14, eff. April
24, 2003; Errata, 19:18 VA.R. 2746, 2747 May 19, 2003; amended, Virginia
Register Volume 22, Issue 7, eff. January 11, 2006; Errata, 22:12 VA.R. 2064
February 20, 2006; amended, Virginia Register Volume 24, Issue 21, eff. August
7, 2008; Volume 25, Issue 12, eff. April 2, 2009.
9VAC25-720-130. New River Basin.
A. Total Maximum Daily Load (TMDLs).
TMDL #
|
Stream Name
|
TMDL Title
|
City/County
|
WBID
|
Pollutant
|
WLA
|
Units
|
1.
|
Stroubles Creek
|
Benthic TMDL for Stroubles Creek in Montgomery County,
Virginia
|
Montgomery
|
N22R
|
Sediment
|
233.15
|
T/YR
|
2.
|
Back Creek
|
Fecal Bacterial and General Standard Total Maximum Daily Load
Development for Back Creek Watershed, Pulaski County, VA
|
Pulaski
|
N22R
|
Sediment
|
0.28
|
T/YR
|
3.
|
Crab Creek
|
Fecal Bacterial and General Standard Total Maximum Daily
Load Development for Crab Creek Watershed, Montgomery County, VA
|
Montgomery
|
N18R
|
Sediment
|
77
|
T/YR
|
4.
|
Peak Creek
|
Fecal Bacterial and General Standard Total Maximum Daily
Load Development for Peak Creek Watershed, Pulaski County, VA
|
Pulaski
|
N17R
|
Copper
|
12
|
KG/YR
|
5.
|
Peak Creek
|
Fecal Bacterial and General Standard Total Maximum Daily
Load Development for Peak Creek Watershed, Pulaski County, VA
|
Pulaski
|
N17R
|
Zinc
|
57
|
KG/YR
|
6.
|
Bluestone River
|
Fecal Bacterial and General Standard Total Maximum Daily Load
Development for Bluestone River
|
Tazewell
|
N36R
|
Sediment
|
116.2
|
T/YR
|
7.
|
Hunting Camp Creek
|
Total Maximum Daily Load (TMDL) Development for Hunting Camp
Creek Aquatic Life Use (Benthic) and E. coli (Bacteria) impairments
|
Bland
|
N31R
|
Sediment
|
0
|
LB/YR
|
8.
|
Chestnut Creek
|
Total Maximum Daily Load Development for Chestnut Creek,
Fecal Bacteria and General Standard (Benthic)
|
Carroll, Grayson
|
N06R
|
Sediment
|
18.9
|
T/YR
|
9.
|
Laurel Fork
|
Benthic TMDL for Laurel Fork, Sussex County, Virginia
|
Tazewell, Pocahontas
|
N37R
|
Sediment
|
21
|
T/YR
|
B. Non-TMDL waste load allocations.
Water Body
|
Permit No.
|
Facility Name
|
Receiving Stream
|
River Mile
|
Outfall No.
|
Parameter Description
|
WLA
|
Units WLA
|
VAS-N11R
|
VA0020281
|
Wytheville WWTP
|
Reed Creek
|
25.79
|
001
|
BOD5
|
360
|
KG/D
|
VAS-N15R
|
VA0089443
|
Hillsville WWTP
|
Little Reed Island Creed
|
25.12
|
001
|
CBOD5, JAN-MAY
|
118
|
KG/D
|
CBOD5, JUN-DEC
|
95
|
KG/D
|
VAW-N21R
|
VA0024040
|
Montgomery Co. PSA - Riner Town - Sewage Treatment
Plant
|
Mill Creek
|
5.12
|
001
|
BOD5
|
7.5
|
KG/D
|
TKN (N-KJEL)
|
1.9
|
KG/D
|
VAW-N22R
|
VA0060844
|
Blacksburg VPI Sanitation Auth. - Lower Stroubles Creek
WWTP
|
New River
|
71.37
|
001
|
BOD5
|
818
|
KG/D
|
VAS-N36R
|
VA0025054
|
Bluefield Westside WWTP
|
Bluestone River
|
25.64
|
001
|
BOD5, JUN-NOV
|
130
|
KG/D
|
BOD5, DEC-MAY
|
260
|
KG/D
|
VAS-N36R
|
VA0062561
|
Tazewell County PSA - Falls Mills Hales Bottom STP
|
Bluestone River
|
22.49
|
001
|
BOD5
|
5.5
|
KG/D
|
VAS-N37R
|
VA0029602
|
Pocahontas STP
|
Laurel Fork
|
1.99
|
001
|
BOD5
|
17
|
KG/D
|
VAW-N21R
|
VA002040
|
Montgomery Co. PSA - Riner Town - Sewage Treatment
Pant
|
Mill Creek
|
5.12
|
001
|
BOD5
|
7.5
|
KG/D
|
TKN (N-KJEL)
|
1.9
|
KG/D
|
VAW-N22R
|
VA0060844
|
Blacksburg VPI Sanitation Auth. - Lower Stroubles Creek
WWTP
|
New River
|
71.37
|
001
|
BOD5
|
818
|
KG/D
|
Statutory Authority
§ 62.1-44.15 of the Code of Virginia and 33 USC § 1313(e) of the
Clean Water Act.
Historical Notes
Derived from Virginia Register Volume 19, Issue 14, eff. April
24, 2003; Errata 19:18 VA.R. 2746, 2747 May 19, 2003; amended, Virginia Register
Volume 20, Issue 24, eff. September 8, 2004; Volume 21, Issue 12, eff. March
23, 2005; Volume 21, Issue 17, eff. June 1, 2005; Volume 22, Issue 2, eff.
November 2, 2005; Volume 22, Issue 6, eff. December 28, 2005; Volume 23, Issue
15, eff. May 2, 2007; Volume 24, Issue 18, eff. June 11, 2008.
9VAC25-720-140. Delegation section.
The director or his designee may perform any action contained in this
regulation except those prohibited by § 62.1-44.14 of the State Water Control
Law.
Statutory Authority
§ 62.1-44.15 of the Code of Virginia and 33 USC § 1313(e) of the Clean Water
Act.
Historical Notes
Derived from Virginia Register Volume 19, Issue 14, eff. April 24, 2003.
|