Iowa DNR
ADBNet

Water Quality Assessments

Impaired Waters List

Nutting Creek IA 01-TRK-205

mouth (S19 T95N R7W Fayette Co.) to confluence with unnamed tributary in S2 T95N R8W Fayette Co.

Assessment Cycle
2014
Result Period
2010 - 2012
Designations
Class A1 Class B(WW-2)
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 5p
Legacy ADBCode
IA 01-TRK-0416_0
Overall Use Support
Not supporting
Aquatic Life Use Support
Fully
Fish Consumption
Not assessed
Primary Contact Recreation
Not supporting
Documentation
Assessment Comments

Assessment based on: (1) results of IDNR/SHL TMDL-related monitoring from June 2006 through June 2007 at TMDL station NuCr1 (STORET station 11330001) and (2) results of IDNR/SHL biological sampling in 2008, 2009 & 2010.

Basis for Assessment

[Note:  Prior to the 2008 Section 305(b) cycle, this stream segment was designated only for Class B(LR) aquatic life uses.   Due to changes in Iowa’s surface water classification that were approved by U.S.  EPA in February 2008, this segment is now presumptively designated for Class A1 (primary contact recreation) uses.   The stream remains designated for aquatic life uses (now termed Class B(WW2) aquatic life uses).   Thus, for the current (2014) assessment, the available water quality monitoring data will be compared to the applicable Class A1 and Class B(WW2) water quality criteria.]

SUMMARY:  The presumptive Class A1 (primary contact recreation) uses remain assessed (monitored) as "not supported" due to levels of indicator bacteria that exceeded state water quality criteria (IR 5p).   The Class B(WW2) aquatic life uses remain assessed (monitored) as "fully supported" (IR 2a) based on results of (1) IDNR/SHL biological sampling in 2008, 2009 & 2010 and (2) IDNR/SHL TMDL-related water quality monitoring from June 2006 to June 2007.   Fish consumption uses remain "not assessed" (IR 3a) due to the lack of fish contaminant monitoring in this river segment.    The sources of data for this assessment include (1) results of IDNR/SHL TMDL-related monitoring from June 2006 through June 2007 at TMDL station NuCr1 (STORET station 11330001) and (2) results of IDNR/SHL biological sampling in 2008, 2009 and 2010.

EXPLANATION:  The presumptive Class A1 (primary contact recreation) uses were assessed (monitored) as "not supported" due to violations of Iowa’s water quality criteria for indicator bacteria.   The geometric mean of E.  coli in the 14 samples collected during the 2006 and 2007 recreational seasons (March 15 to November 15) at TMDL station NuCr1 was 4,087 orgs/100 ml.; ten of the 14 samples (71%) exceeded Iowa’s 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 the geometric mean of E.  coli is greater than the state criterion of 126 orgs/100 ml., the primary contact recreation uses should be assessed as "not supported" (see pgs 3-33 to 3-35of U.S.  EPA 1997b).  

The results of IDNR/SHL water quality monitoring at TMDL station NuCr1 from June 2006 to 2007 suggest “full support” of the Class B(WW2) aquatic life uses.   None of the 13 samples collected violated the Class B(WW2) criteria for dissolved oxygen, pH, or ammonia.  

This assessment is also based on biological data collected in 2008, 2009 and 2010 as part of the IDNR/SHL stream biocriteria project.   A series of biological metrics which reflect stream water quality and habitat integrity were calculated from the biocriteria 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 2008 FIBI score was 55 (good) and the BMIBI score was 75 (good).   The 2009 FIBI score was 65 (good) and the BMIBI score was 74 (good).   The 2010 FIBI score was 65 (good) and the BMIBI score was 77 (excellent).   The aquatic life use support was assessed as fully supporting (=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 1994-2004.   The FIBI BIC for this ecoregion is 52 and the BMIBI BIC for this ecoregion is 61.   This segment passed the FIBI and BMIBI BICs 3/3 times in the last five years.   This aquatic life use assessment is considered "monitored" because there were two or more samples collected in multiple years over a recent five-year period.

Fish consumption uses remain "not assessed" due to the lack of fish contaminant monitoring in this river segment.

Monitoring and Methods
Assessment Key Dates
9/13/2010 Biological Monitoring
9/21/2009 Biological Monitoring
10/6/2008 Biological Monitoring
6/20/2007 Fixed Monitoring End Date
6/29/2006 Fixed Monitoring Start Date
Methods
220 Non-fixed station physical/chemical monitoring (conventional pollutant only)
315 Regional reference site approach
330 Fish surveys
380 Quan. measurements of instream parms-- channel morphology-- floodplain-- 1-2 seasons-- by prof
320 Benthic macroinvertebrate surveys
420 Water column surveys (e.g. fecal coliform)
Monitoring Levels
Biological 4
Habitat 4
Physical Chemistry 1
Toxic 0
Pathogen Indicators 2
Other Health Indicators 0
Other Aquatic Life Indicators 0
# of Bio Sites 2
BioIntegrity Good
Causes and Sources of Impairment
Causes Use Support Cause Magnitude Sources Source Magnitude
Pathogens Primary Contact Recreation High
  • Source Unknown
  • High