Bear Creek IA 02-CED-523
mouth (S21 T86N R10W Benton Co.) to confluence with unnamed tributary in SW 1/4 S34 T88N R9W Buchanan Co.
- Cycle
- 2018
- Release Status
- Final
- Overall IR
- 5 - Water is impaired or threatened and a TMDL is needed.
- Trend
- Unknown
- Created
- 5/13/2019 12:50:38 PM
- Updated
- 8/2/2019 1:34:13 PM
The presumptive Class A1 (primary contact recreation) uses remain assessed as “not supported” due to violations of Iowa water quality criteria for indicator bacteria. The source of data for this assessment remains the results of chemical, physical, and bacterial monitoring at 52nd St. Dr. (STORET station 15060002) from May 2010 to July 2011. The Class B(WW2) aquatic life uses are assessed (evaluated) as "fully supported" based on results of DNR/SHL biological sampling in 2009, 2010 and 2013.
The presumptive Class A1 (primary contact recreation) uses are assessed (evaluated) as "not supported" based on levels of indicator bacteria that exceeded state water quality criteria. The geometric means of indicator bacteria (E. coli) in the 11 samples at 52nd St. Dr. (STORET station 15060002) collected during the recreational season of 2010 (495 orgs/100 ml), and the geometric mean of the 12 samples collected during the recreation season of 2011 (1,079 orgs/100 ml) both exceeded the Class A1 criterion of 126 orgs/100 ml. Twenty-one of the combined 23 samples (91%) exceeded Iowa’s single-sample maximum criterion of 235 orgs/100 ml. According to U.S. EPA guidelines for Section 305(b) reporting and 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).
The Class B(WW2) aquatic life uses are assessed (evaluated) as "fully supporting" based on biological data collected in 2009, 2010 and 2013 as part of the DNR/SHL stream biocriteria project. A series of biological metrics which reflect stream water quality and habitat integrity were calculated from the biological sampling data. The biological metrics are based on the numbers and types of benthic macroinvertebrate taxa and fish species that were collected in the stream sampling reach. The biological metrics were combined to make a fish community index of biotic integrity (FIBI) and a benthic macroinvertebrate index (BMIBI). The indexes rank the biological integrity of a stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum). The 2009 FIBI score was 66 (good) and the BMIBI score was 79 (excellent). The 2010 FIBI score was unavailable and the BMIBI score was 78(excellent). The 2013 FIBI score was 82(excellent) and the BMIBI score was 63 (good). The aquatic life use support was assessed as fully supported (=FS), based on a comparison of the FIBI and BMIBI scores with biological impairment criteria (BIC) established for previous Section 305(b) reports. The biological impairment criteria were determined from a statistical analysis of data collected at stream ecoregion reference sites from 1994-2008. The riffle habitat FIBI BIC for this ecoregion is 65 and the natural substrate BMIBI BIC for this ecoregion is 70. This segment passed the FIBI BIC 2/2 times and passed the BMIBI BIC 2/3 times in the last eight years (2009-2016). This assessment is now considered "evaluated" because to complete the assessment, data greater than five years old (2009, 2010) were used to complete the assessment.
The results of chemical/physical monitoring at 52nd St. Dr. in 2010 and 2011 indicated good chemical water quality in this stream segment and “full support” of the Class B(WW2) aquatic life uses; thus, these results are consistent with the biological assessment for this segment. No violations of Class B(WW2) water quality criteria for dissolved oxygen, pH or temperature occurred in the 23 samples analyzed from May 2010 to July 2011. These results suggest that the Class B(WW2) aquatic life uses should be assessed (evaluated) as “fully supported.”