Crane Creek IA 01-TRK-211
from confluence with unnamed tributary (NE 1/4 NW 1/4 S4 T95N R11W Chickasaw Co.) to confluence with Spring Cr. in S17 T98N R12W Howard Co.
- Cycle
- 2018
- Release Status
- Final
- Overall IR
- 5 - Water is impaired or threatened and a TMDL is needed.
- Trend
- Unknown
- Created
- 7/18/2019 12:37:37 PM
- Updated
- 7/18/2019 12:38:29 PM
The presumptive Class A1 (primary contact recreation) uses are assessed (monitored) as “not supported” due to levels of indicator bacteria that exceed state water quality criteria. The Class B(WW1) aquatic life uses are assessed (monitored) as “fully supported” based on results of water quality monitoring from April 2012 to November 2014. Fish consumption uses remain "not assessed" due to the lack of fish contaminant monitoring in this assessment segment. The source of data for this assessment is the results of monitoring from the Turkey River Watershed project from April 2012 to November 2014 at station CRA40 at 120th Street (STORET station 15190001).
The presumptive Class A1 (primary contact recreation) uses are assessed as "not supported" based on levels of indicator bacteria that exceeded state water quality criteria. Based on the approximately eight monthly samples collected during the recreation seasons of 2012, 2013, and 2014, the geometric means at station CRA-40 are as follow: 601, 1,968, and 486 E. coli orgs/100 ml., respectively. All three geometric means exceed the Class A1 criterion of 126 orgs/100 ml. Twenty of the combined 23 samples (87%) 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 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.”
Results of chemical/physical water quality monitoring conducted at station CRA-40 from April 2012 to November 2014 show no violations of Class B(WW1) water quality criteria for dissolved oxygen (24 samples), ammonia (16 samples), pH (24 samples), temperature (24 samples), or chloride (16 samples). Thus, these monitoring results suggest that the Class B(WW1) aquatic life uses should be assessed (monitored) as “fully supported”.
The Class HH (human health/fish consumption) uses remain “not assessed” due to the lack of fish contaminant monitoring in this assessment segment.