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Surface Water - Alabama Department of Environmental Management

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Cahaba River (0315-0202)<br />

suspended solids were periodically elevated. Fecal coliform concentrations were≥1,000<br />

colonies/100 mL during May <strong>of</strong> 2002 and April <strong>of</strong> 2003. A WWTP is upstream <strong>of</strong> the site<br />

and a sewage smell in the sediments was observed. Similar results were obtained during<br />

ADEM’sAmbient Monitoring Program from June <strong>of</strong> 2000 through August <strong>of</strong> 2002<br />

(Appendix R).<br />

Intensive water quality sampling conducted during ADEM’s Ambient Monitoring<br />

Program on the Cahaba River at C3 indicated elevated nutrient concentrations and<br />

periodically elevated total suspended solid concentrations (Appendix R).<br />

At GSACR-4, Cahaba River is a riffle-run stream located in the Southern Sandstone<br />

Ridges (Appendix E). The reach was dominated by cobble and bedrock runs. Riffle<br />

habitat was less available, and characterized by cobble, gravel, and sand. Pools were sandcovered<br />

bedrock. The fish community was assessed as fair at this location. (O’Neil 2002,<br />

Appendix G).<br />

Sub-watershed status: Biological conditions were impaired at Piney Murry Creek, Savage<br />

Creek, and the Cahaba River (Appendix G). Habitat quality at Savage Creek and the<br />

Cahaba River were affected by sedimentation. SWCD estimates also indicated mining and<br />

pasture run<strong>of</strong>f to be potential sources <strong>of</strong> impairment within the sub-watershed. Elevated<br />

conductivities at Piney Murry and Savage Creek may be caused by mining within the subwatershed.<br />

Biological conditions at Cahaba River locations were impacted by<br />

sedimentation and nutrient enrichment. SWCD landuse estimates indicate the impairment<br />

to be from urban sources.<br />

67

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