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 Daily 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 |
60. | South River | Bacteria and Benthic Total Maximum Daily Load Development for South River | Augusta and Rockingham | B32R | Sediment | 619.4 | T/YR |
61. | South River | Bacteria and Benthic Total Maximum Daily Load Development for South River | Augusta and Rockingham | B32R | Phosphorus | 6,929.9 | KG/YR |
62. | South River | Total Maximum Daily Load Development for Mercury in the South River, South Fork Shenandoah River, and Shenandoah River, Virginia | Augusta, Rockingham, Page, and Warren | B32R | Mercury | 112 | G/YR |
63. | South Fork Shenandoah River | Total Maximum Daily Load Development for Mercury in the South River, South Fork Shenandoah River, and Shenandoah River, Virginia | Augusta, Rockingham, Page, and Warren | B32R, B33R | Mercury | 112 | G/YR |
64. | Shenandoah River | Total Maximum Daily Load Development for Mercury in the South River, South Fork Shenandoah River, and Shenandoah River, Virginia | Augusta, Rockingham, Page, and Warren | B32R, B33R | Mercury | 112 | G/YR |
65. | Spout Run | Total Maximum Daily Load Development to Address Bacteria and Benthic Impairments in the Spout Run Watershed, Clarke County, Virginia | Clarke | B57R | Sediment | 7.44 | T/YR |
66. | West Strait Creek | Benthic Total Maximum Daily Load Development for Strait Creek and West Strait Creek | Highland | B02R | Sediment | 0.02 | T/D |
67. | West Strait Creek | Benthic Total Maximum Daily Load Development for Strait Creek and West Strait Creek | Highland | B02R | CBOD5 | 11 | KG/D |
68. | West Strait Creek | Benthic Total Maximum Daily Load Development for Strait Creek and West Strait Creek | Highland | B02R | Dry season (June – December) ammonia as N | 1.6 | KG/D |
69. | West Strait Creek | Benthic Total Maximum Daily Load Development for Strait Creek and West Strait Creek | Highland | B02R | Wet season (January – May) ammonia as N | 2.9 | KG/D |
70. | Strait Creek | Benthic Total Maximum Daily Load Development for Strait Creek and West Strait Creek | Highland | B02R | Sediment | 0.08 | T/D |
B. Non-TMDL waste load allocations.
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.
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.
(11) Opequon WRF: (a) the TN WLA is derived based on 3 mg/l of TN and 12.6 MGD; (b) the TN WLA includes an additional allocation for TN in the amount of 6,729 lbs/yr by means of a landfill leachate consolidation and treatment project; and (c) the TP WLA is derived based on 0.3 mg/l of TP and 12.6 MGD.