Cedar River IA 02-CED-455
from Prairie Cr. (SE 1/4 S34 T83N R7W Linn Co.) to confluence with McCloud Run in SW 1/4 S16 T83N R7W Linn Co.
- Cycle
- 2018
- Release Status
- Final
- Overall IR
- 4 - Water is impaired or threatened and a TMDL has been completed or is not needed.
- Trend
- Unknown
- Created
- 8/1/2019 2:42:07 PM
- Updated
- 12/13/2019 2:36:12 PM
SUMMARY: The Class A1 (primary contact recreation) uses are assessed (monitored) as "partially supported" (IR 4a) due to levels of indicator bacteria that very slightly exceed state water quality criteria. Results of ambient chemical/physical water quality monitoring suggest that the Class B(WW1) aquatic life uses should be assessed (monitored) as "fully supported.” Fish consumption uses remain assessed (monitored) as “fully supported” (IR 2a) based on results of fish contaminant monitoring in 2006. The sources of data for this assessment include (1) the results of monthly monitoring from 2014 through 2016 at the IDNR/UHL ambient city monitoring station located at the Highway 30 bridge downstream from Cedar Rapids (station 10570001), (2). The water quality data is the same data used to develop the assessment for the adjacent downstream segment of the Cedar River (IA 02-CED-451).
Note: A TMDL for indicator bacteria in this segment of Cedar River was prepared and approved by EPA in February 2010. The approval of this TMDL moved the bacterial impairment for this segment from Iowa's list of Section 303(d) waters (Category 5a of the Integrated Report) to IR Category 4a (impaired; TMDL not required). The Class A1 (primary contact recreation) uses are assessed (monitored) as "partially supported" based on levels of indicator bacteria that exceeded state water quality criteria. The geometric means of indicator bacteria (E. coli) in the 23 samples collected during the recreational seasons of 2014 through 2016 at Station 10570001 Cedar River Downstream of Cedar Rapids (DS1) were as follows: the 2014 geometric mean was 131 orgs/100 ml, the 2015 geometric mean was 277 orgs/100 ml, and the 2016 geometric mean was 233 orgs/100 ml. All three recreation season geometric means exceeded the Class A1 geometric mean criterion of 126 orgs/100 ml. Ten of the combined 23 samples (43%) exceeded Iowa’s Class A1 single-sample maximum criterion of 235 orgs/100 ml. According to U.S. EPA guidelines for Section 305(b) reporting and Iowa DNR’s assessment/listing methodology, if the geometric mean is greater than 126 orgs/100 ml., the primary contact recreation uses should be assessed as "impaired" (see pgs 3-33 to 3-35 of U.S. EPA 1997b). Thus, because at least one recreation season geometric mean exceeded criteria for Class A1 uses, these uses are assessed as "partially supported." Results of chemical/physical water quality monitoring at Station 10570001 Cedar River Downstream of Cedar Rapids (DS1) suggest “full support” of the aquatic life uses. Monitoring showedno violations of Class B(WW1) water quality criteria for 34 Ammonia samples (maximum = 1.3 mg/L), 35 Dissolved Oxygen samples (minimum = 7.6 mg/L), 34 pH samples (range = 7.4 to 8.7), 35 Temperature samples (maximum = 26.5°C), 35 Chloride samples (maximum = 59 mg/L), or 35 Sulfate samples (maximum = 69 mg/L) occurred during monitoring from January 2014 to December 2016. According to U.S. EPA guidelines for Section 305(b) water quality assessments (U.S. EPA 1997b, page 3-17), the EPA guidelines allow up to 10% violations of these conventional parameters before impairment of water quality is indicated. Thus, these results thus suggest “full support” of the Class B(WW1) aquatic life uses.
Fish consumption uses remain assessed (monitored) as “fully supported” based on results of U.S.EPA/DNR fish contaminant (RAFT) monitoring at Cedar Rapids in 2006. The existence of, or potential for, a fish consumption advisory is the basis for Section 305(b) assessments of support of fish consumption uses in Iowa’s rivers and lakes. The composite samples of fillets from channel catfish and freshwater drum had low levels of contaminants. Levels of primary contaminants in the composite sample of channel catfish fillets were as follows: mercury: 0.0803 ppm; total PCBs: 0.091 ppm; and technical chlordane: 0.03 ppm. Levels of primary contaminants in the composite sample of freshwater drum fillets were as follows: mercury: 0.104 ppm; total PCBs: 0.09 ppm; and technical chlordane: 0.03 ppm. All levels of these contaminants from this monitoring are below advisory trigger levels, thus suggesting the continued “full support” of fish consumption uses in this segment of the Cedar River.