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

See Also

Overview of the TMDL Process

Beaver-Camas Creek Subbasin TMDL Contact

Troy Saffle
DEQ Idaho Falls

Regional Office

900 N. Skyline, Suite B
Idaho Falls, ID 83402
ph: (208) 528-2650

fx: (208) 528-2695
troy.saffle@deq.idaho.gov



Surface Water: Beaver-Camas Subbasin

Assessment and Total Maximum Daily Loads

> Link to document
 The Subbasin at a Glance
Hydrologic Unit Code 17040214
Size 643,083 acres (1,005 square miles)
§303(d) Listed Stream
Segments
Camas Creek (2 segments), Beaver Creek (2 segments), Cow Creek
Beneficial Uses Affected Cold water, salmonid spawning, primary/secondary contact recreation, domestic water supply
Pollutants of Concern Nutrients, sediment, temperature, flow alteration, habitat alteration
Major Land Uses Range, irrigated agriculture, forestry
Date Approved by U.S. EPA August 2005
 
 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

The Beaver-Camas Subbasin of southeast Idaho is a watershed of the Upper Snake River Basin. The watershed is the easternmost in a series of five "sinks drainages." The subbasin is dominated by both natural and human-caused flow alterations.

 

Data have been collected and analyzed to evaluate the scope of the water quality limiting issues on §303(d) listed and non-listed streams. Seven temperature TMDLs and one sediment TMDL have been developed in response to the data. Some TMDLs have been established for non-listed streams since water quality data show that there are exceedances of Idaho's water quality standards.

 

Stream bank erosion, reduced riparian vegetation, and low flow conditions are the causes of increased water temperatures in the subbasin. Riparian grazing is the principal source of temperature and sediment loading to the watershed. Elevated temperatures from reduced riparian vegetation and accelerated stream bank erosion have been exacerbated by an ongoing drought.

 

There are two §303(d) listed segments on Beaver Creek. Temperatures in the upper segment of the creek exceed the state standard and a TMDL was developed. Perennial flows are seldom seen in the lower segment; therefore, it is proposed to be de-listed for all currently listed pollutants and re-listed only as flow altered.

 

Camas Creek is §303(d) listed from its headwaters to its mouth (as two segments). Riparian grazing has contributed to bank erosion and elevated stream temperatures. Sediment and temperature TMDLs have been calculated to address the pollutants of concern in the upper segment. The lower segment of Camas Creek is intermittent and flow altered for irrigation; therefore, it is recommended this segment be listed only as flow altered. No TMDLs were developed for the lower segment.

 

Cow Creek is §303(d) listed, but is an ephemeral stream and therefore should be de-listed; ephemeral streams are not expected to support the same biological communities as perennial waters.

 

Dairy, East Fork Camas, Modoc, Threemile, and West Fork Camas Creeks are not §303(d) listed. However, stream temperature data show that there were major exceedances in Idaho's numeric temperature criteria in these creeks. Temperature TMDLs were established for all five streams.

 

TMDLs were not developed for streams listed as flow or habitat altered. The EPA does not believe that flow or habitat alteration are pollutants as defined by the Clean Water Act. Since TMDLs are not required for water bodies impaired by pollution but not pollutants, TMDLs were not developed for flow or habitat altered streams.

 
 Streams and Pollutants for Which TMDLs Were Developed
Beaver Creek Temperature
Camas Creek Sediment, temperature
Dairy Creek Temperature
East Camas Creek Temperature
Modoc Creek Temperature
Threemile Creek Temperature
West Camas Creek Temperature
 
 Subbasin Assessment and TMDLs
View entire document (pdf 7.6 mb, 252 pages)

Because of the large size of this pdf document, we have also divided it into sections for quicker download.

Prefatory Material: Cover; Acknowledgments; Table of Contents (including Lists of Tables, Figures, and Appendices); Abbreviations, Acronyms, and Symbols; Executive Summary 240 kb, 28 pages
Chapter 1:

Subbasin Assessment - Watershed Characterization (including maps)

Subbasin Assessment - Watershed Characterization (text only)

3.1 mb, 52 pages

 

1.5 mb, 33 pages

Chapter 2:

Subbasin Assessment - Water Quality Concerns and Status (including maps)

Subbasin Assessment - Water Quality Concerns and Status (text only)

3.0 mb, 45 pages

 

420 kb, 37 pages

Chapter 3: Subbasin Assessment - Pollutant Source Inventory 18 kb, 2 pages
Chapter 4: Subbasin Assessment - Summary of Past and Present Pollution Control Efforts 14 kb, 2 pages
Chapter 5: Total Maximum Daily Loads 963 kb, 28 pages
Supporting Documentation: References, Glossary 76 kb, 24 pages
Appendices: Appendices A - L 356 kb, 71 pages
 



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