Black Hawk Creek IA 02-CED-545
mouth (S22 T89N R13W Black Hawk Co.) to Hwy 58 in E 1/2 S27 T88N R14W Black Hawk Co.)
- Assessment Cycle
- 2016
- Release Status
- Final
- Data Collection Period
- Overall IR Category
- 4 - Water is impaired or threatened and a TMDL has been completed or is not needed.
- Trend
- Unknown
- Created
- 8/16/2016 3:07:27 PM
- Updated
- 8/16/2016 3:07:27 PM
Assessment Summary
The Class A1 (primary contact recreation) uses are assessed (monitored) as "partially supported" (IR 4a) due to continued levels of indicator bacteria that violate state water quality standards. The Class B(WW1) aquatic life uses are assessed (monitored) as "fully supported" (IR 2a) based on results of ambient water quality monitoring. Fish consumption uses remain assessed (evaluated) as "fully supported" (IR 2a) based on results of fish contaminant monitoring in 2004. Sources of data for this assessment include (1) results monthly monitoring from January 2012 through December 2014 at the IDNR ambient station at Ridgeway Avenue SW of Waterloo (station 10070004) and (2) U.S. EPA/IDNR fish tissue (RAFT) monitoring in 2004 near Hudson.
Assessment Explanation
Note: A TMDL for indicator bacteria in this segment of Black Hawk Creek was prepared by IDNR and approved by EPA in 2006. Because all Section 303(d) impairments identified for the 2008 assessment/listing cycle (indicator bacteria) are addressed by the TMDL, this waterbody is placed in IR Category 4a (impaired; TMDL approved) of the current Integrated Report.
EXPLANATION: The Class A1 (primary contact recreation) uses are assessed as "partially supported" due to levels of indicator bacteria (E. coli) that violated Iowa’s Class A1 water quality criteria during recreational seasons of 2012, 2013 and 2014. The geometric means of indicator bacteria (E. coli) in the 24 monthly samples collected during the recreational seasons of 2012 through 2014 at station 10070004 at Waterloo were as follows: the 2012 geometric mean was 247 orgs/100 ml, the 2013 geometric mean was 192 orgs/100 ml and the 2014 geometric mean was 108 orgs/100 ml. The 2012 and 2013 geometric means slightly exceed the Class A1 criterion of 126 orgs/100 ml; the 2014 geometric mean was below this criterion. Eight of the 24 monthly samples (33%) exceeded the Class A1 single-sample maximum criterion of 235 orgs/100 ml. According to U.S. EPA guidelines for Section 305(b) reporting and IDNR’s assessment/listing methodology, if a recreation season geometric mean exceeds the respective water quality criterion, the 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 impaired.
The Class B(WW1) aquatic life uses are assessed (monitored) as "fully supported" based on results of monitoring from the IDNR/UHL ambient station SW of Waterloo (STORET Station 10070004) from 2012 through 2014. Monitoring at this station showed no violations of Class B(WW1) water quality criteria for dissolved oxygen, pH, temperature, ammonia-nitrogen, chloride, or sulfate in the 36 monthly samples analyzed during the 2012-2014 monitoring period. These monitoring results suggest that the Class B(WW2) aquatic life uses should be assessed as “fully supporting”.
Fish consumption uses remain assessed (evaluated) as “fully supported” based on results of U.S.EPA/IDNR fish contaminant (RAFT) monitoring near Hudson in 2004. The composite samples of fillets from channel catfish and smallmouth bass had very low levels of contaminants. Levels of primary contaminants in the composite sample of channel catfish fillets were as follows: mercury: 0.072 ppm; total PCBs: 0.092 ppm; and technical chlordane: 0.044 ppm. Levels of primary contaminants in the composite sample of smallmouth bass fillets were as follows: mercury: 0.098 ppm; total PCBs: 0.09 ppm; and technical chlordane: < 0.03 ppm. The existence of, or potential for, a fish consumption advisory is the basis for Section 305(b) assessments of the degree to which Iowa’s lakes and rivers support their fish consumption uses. The levels of contaminants do not exceed any of the Iowa advisory trigger levels, thus suggesting no justification for issuance of a consumption advisory.
Assessment Key Dates
9/2/2004 | Fish Tissue Monitoring |
1/5/2012 | Fixed Monitoring Start Date |
12/31/2014 | Fixed Monitoring End Date |
Methods
230 | Fixed station physical/chemical (conventional plus toxic pollutants) |
260 | Fish tissue analysis |
420 | Indicator bacteria monitoring |