Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Coldwater Creek IA 01-UIA-280

mouth (S32 T100N R9W Winneshiek Co.) to north line of S31 T100N R9W Winneshiek Co.

Cycle
2016
Release Status
Final
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Unknown
Created
6/6/2016 4:42:04 PM
Updated
10/5/2016 7:43:58 AM
Use Support
Class A1
Recreation - Primary contact
Partially Supported
Support Level
Partially Supported
Impairment Code
5p - Impairment occurs on a waterbody with a presumptive A1 or B(WW1) use.
Cause Magnitude
Moderate
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2008
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Watershed project monitoring
TMDL Priority
Tier III
Class A2
Recreation - Secondary contact
Partially Supported
Support Level
Partially Supported
Impairment Code
5p - Impairment occurs on a waterbody with a presumptive A1 or B(WW1) use.
Cause Magnitude
Moderate
Status
New
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2016
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Watershed project monitoring
TMDL Priority
Tier III
Class BCW1
Aquatic Life - Cold Water Type 1
Fully Supported
Class HH
Human Health -
Not Assessed
General Use
General Use water -
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The presumptive Class A1 (primary contact recreation) uses are assessed (monitored) as “partially supported” (IR 5p) due to levels of indicator bacteria that exceed state water quality criteria.  The presumptive Class A2 (secondary contact recreation) uses are also assessed (monitored) as “partially supported” (IR 5p):  this is a new impairment for this assessment segment.  The Class B(CW1) coldwater aquatic life uses are assessed (monitored) as "fully supported" (IR 2a) based on results of biological sampling in 2007 and 2011, results of water quality monitoring from 2012 and 2014, and an updated summary of trout reproduction in Iowa streams prepared by the IDNR Fisheries Bureau in January 2016.  Fish consumption uses remain “not assessed” (IR 3a) due to the lack of fish contaminant monitoring in this stream segment.  The sources of data for this assessment include (1) the results of monitoring for indicator bacteria conducted at Site 9 of the Upper Iowa River Watershed (UIRW) project (STORET No.  NEIARCD 191910003) from April 2012 through October 2014, (2) results of DNR/SHL biological sampling in 2007 and 2011 and (3) an updated summary of trout reproduction in Iowa streams prepared by the IDNR Fisheries Bureau in January 2016. 

Assessment Explanation

The presumptive Class A1 (primary contact recreation) uses and Class A2 (secondary contact recreation uses are assessed (monitored) as impaired (partially supporting) due to violations of Iowa’s water quality criteria for indicator bacteria.  The geometric means of indicator bacteria (E. coli) in the 21 samples collected during the recreational seasons of 2012 through 2014 at UIRW Site 9 were as follows:  the 2012 geometric mean was 131 orgs/100 ml, the 2013 geometric mean was 188 orgs/100 ml, and the 2014 geometric mean was 1,231 orgs/100 ml.  All three geometric means exceed the Class A1 criterion of 126 orgs/100 ml, and the 2014 geometric mean exceeds the Class A2 geometric mean criterion of 630 orgs/100 ml.  Nine of the 21 samples (43%) exceeded the Class A1 single-sample maximum criterion of 235 orgs/100 ml; four of the 21 samples (19%) exceeded the Class A2 single-sample maximum criterion of 2,880 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, the presumptive Class A1 and Class A2 uses are assessed (monitored) as impaired. 

The assessment of the Class B(CW1) aquatic life uses remains, in part, based on data collected in 2007 and 2011 as part of the IDNR/SHL coldwater stream sampling project.  A series of biological metrics which reflect coldwater 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 that were collected in the stream sampling reach.  The biological metrics were combined to make a coldwater benthic index (CBI).  The index ranks the biological integrity of a coldwater stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum).  The 2007 CBI score was 81 and the 2011 CBI score was 81.  The aquatic life use support was assessed (monitored) as fully supporting (=FS), based on a comparison of the CBI scores with biological impairment criteria (BIC) established for the 2012 Section 305(b) report.  The biological impairment criteria were determined from a statistical analysis of data collected at coldwater stream reference sites from 1994-2011.  The CW BIC is 60 and this segment passed the CW BIC 2/2 times in a recent five-year period (2007-2011). 

An updated summary of trout reproduction in Iowa streams prepared by the IDNR Fisheries Bureau in January 2016 also suggests that the Class B(CW1) uses should be assessed as "fully supported".  According to the updated summary, (Unnamed) Cold Water Creek is in the group of Iowa coldwater streams that supports natural reproduction of trout.  Based on results of surveys by the IDNR Fisheries Bureau, this stream is placed in the category (I) of Iowa trout streams that exhibit fairly consistent natural reproduction and maintain a viable population of the listed species without any stocking for one species of trout (Brown Trout) and in the category of streams (II) that exhibit recent, but inconsistent reproductive success and that are generally not capable of maintaining a viable population for the resident trout species at this time for a second species of trout (Rainbow Trout).  This assessment is consistent with previous assessments of the ability of this stream to support natural reproduction of trout. 

In addition, the Class B(CW1) coldwater aquatic life uses are assessed as “fully supported” based on results of water quality monitoring from 2012 to 2014.  Thirteen of the 14 samples analyzed for ammonia from April 2012 to October 2014 contained less than the limit of detection (0.05 mg/l); the one detected level (0.08 mg/l) is well below Class B(CW1) criteria.  None of the 14 samples violated the Class B(CW1) criteria for temperature.  Two of the 13 samples (15%) analyzed for pH exceeded the Class B(CW1) criterion of 9.0 pH units.  According to U.S. EPA guidelines for Section 305(b) reporting and IDNR’s assessment/listing methodology, if significantly greater than 10% of samples exceed criteria for conventional parameters such as pH, the assessed uses should be assessed as “impaired”.  According to Iowa DNR’s assessment methodology, however, the percentage of samples that exceeded the Class B(CW1) pH criterion of 9.0 units during the 2012-2014 assessment period at Site 9 was not significantly greater than 10%.  Thus, these results do not suggest impairment of the Class B(CW1) aquatic life uses. 

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

Monitoring and Methods
Assessment Key Dates
1/1/2016
Biological Monitoring
4/3/2012
Fixed Monitoring Start Date
10/7/2014
Fixed Monitoring End Date
7/16/2007
Biological Monitoring
8/16/2011
Biological Monitoring
Methods
120
Surveys of fish and game biologists/other professionals
220
Non-fixed station physical/chemical monitoring (conventional pollutant only)
315
Regional reference site approach
320
Benthic macroinvertebrate surveys
380
Quantitative physical habitat assessment
420
Indicator bacteria monitoring