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List of Subbasin Assessments, TMDLs, and Implementation Plans in Idaho

See Also

Overview of the TMDL Process

Upper Snake Rock TMDL Contact

Balthasar "Sonny" Buhidar

DEQ Twin Falls

Regional Office

1363 Fillmore Street

Twin Falls, ID 83301

ph: (208) 736-2190

fx: (208) 736-2194

balthasar.bihudar@deq.idaho.gov



Surface Water: Upper Snake Rock
Watershed Management Plan

> Link to document
> Link to Aquaculture Wasteload Allocations
 Upper Snake Rock Watershed Management Plan at a Glance
Hydrologic Unit Code 17040212
Size 2,438 square miles (1,536,880 acres)
§303(d) Listed
Stream Segments
Alpheus Creek, Billingsley Creek, Blind Canyon Creek, Clear Springs, Clover Creek, Cottonwood Creek, Crystal Springs, Dry Creek (2 segments), Dry Creek (West Fork), Ellison Creek, McMullen Creek, Riley Creek, Rock Creek, Thousand Springs Creek, Vinyard Creek, Bliss Reservoir, Lower Salmon Falls Reservoir, Pioneer Reservoir, Shoshone Falls Reservoir, Upper Salmon Falls Reservoir, Middle Snake River (10 segments)
Beneficial Uses Affected Cold water biota, salmonid spawning, primary and secondary contact recreation
Pollutants of Concern Sediment, nutrients (phosphorus and nitrogen), pathogens (fecal coliform bacteria), ammonia, pesticides, oil and grease
Major Land Uses Rangeland, agriculture
Date Approved by U.S. EPA August 2000
 
 Background
The federal Clean Water Act requires that states and tribes restore and maintain the chemical, physical, and biological integrity of the nation's waters. States and tribes must adopt water quality standards necessary to protect fish, shellfish, and wildlife while providing for recreation in and on the waters whenever possible.

Section 303(d) of the Clean Water Act establishes requirements for states and tribes to identify and prioritize water bodies that are water quality limited (i.e., water bodies that do not meet water quality standards). States and tribes must periodically publish a priority list of impaired waters, currently every two years. For waters identified on this list, states and tribes must develop water quality improvement plans known as total maximum daily loads (TMDLs) that establish allowable pollutant loads set at levels to achieve water quality standards.

 
 Overview
Thirty-one water bodies/stream segments in the Upper Snake Rock Subbasin were listed on the 1996 §303(d) list, including 10 segments of the middle Snake River. The TMDL covers 93 miles of the Snake River, including 28 named tributaries.

The middle Snake River TMDL also covers portions of this subbasin.

The middle Snake River is a managed water system where normal flow regimes are no longer present, which allows sediment to accumulate. In general, the middle Snake River and its tributaries are impacted by runoff from irrigated crop production, rangeland, pastureland, animal holding areas, feedlots, dredging, hydro-modification, and urban runoff. Natural springs have exhibited hydro-modification and stream bank modification from activities relating to sedimentation, aquaculture, hydropower, irrigated crop production, and land development.

TMDLs were not written for ammonia, nitrogen, pesticides, oil and grease, or temperature. Data did not show that nitrogen, pesticides, or oil and grease were exceeding water quality standards or impacting beneficial uses. It will be recommended that pesticides and oil and grease be removed from the §303(d) list; nitrogen levels will continue to be reviewed by DEQ. Clover Creek was found to be polluted by ammonia, but ammonia is not listed on the §303(d) list for Clover Creek. It will be recommended that ammonia be added to the next §303(d) list for Clover Creek; a TMDL will be completed after this occurs. Temperature TMDLs have been deferred until after new water quality standards are developed for temperature (new standards are projected to be proposed in 2000).

 
  Streams and Pollutants for Which TMDLs Were Developed
Alpheus Creek Sediment (total suspended solids), phosphorus
Billingsley Creek Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Blind Canyon Creek Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Cedar Draw Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Clear Springs Sediment (total suspended solids), phosphorus
Clover Creek Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Cottonwood Creek Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Crystal Springs Sediment (total suspended solids), phosphorus
Deep Creek Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Dry Creek
(2 segments)
Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Dry Creek
(West Fork)
Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Ellison Creek Sediment (total suspended solids), phosphorus
McMullen Creek Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Mud Creek Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Riley Creek Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Rock Creek Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Thousand Springs Creek Sediment (total suspended solids), phosphorus
Vinyard Creek Sediment (total suspended solids), phosphorus
Bliss Reservoir Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Lower Salmon Falls
Reservoir
Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Pioneer Reservoir Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Shoshone Falls Reservoir Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Upper Salmon Falls
Reservoir
Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
Middle Snake River
(10 segments)
Sediment (total suspended solids), pathogens (fecal coliform bacteria), phosphorus
 
 Watershed Management Plan

This document is not available electronically. To view a hard copy, contact DEQ's Upper Snake Rock Watershed TMDL contact.

 
 Aquaculture Wasteload Allocations

Draft wasteload allocations for aquaculture facilities were developed in July 2004. These allocations are designed to meet the total phosphorus reductions as specified in the Middle Snake River and Upper Snake Rock TMDLs. The allocations affect 37 TMDLs for total phosphorus and total suspended solids and six associated segments of the Snake River.


Public comments were accepted on the document in August 2004. In spring 2005, DEQ invited public comment on the document's aquaculture wasteload allocations separately in three parts. The aquaculture wasteload allocations were submitted to EPA for review in August 2005.

View Upper Snake Rock Watershed Management Plan – Modification - A Modification of Mid-Snake TMDL and Upper Snake Rock TMDL to Account for the Aquaculture Wasteload Allocation of Part 1 (Fish Production Facilities and Conservation Hatcheries), Part 2 (Fish Processors), and Part 3 (Billingsley Creek Facilities) (pdf 936 kb, 171 pages).




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