Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Whitewater Creek IA 01-NMQ-103

mouth (S10 T86N R1W Jones Co.) to confluence with Curran Branch in S12 T87N R1W Dubuque Co.

Cycle
2016
Release Status
Final
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Unknown
Created
3/28/2016 4:10:45 PM
Updated
11/16/2016 3:40:58 PM
Use Support
Class A1
Recreation - Primary contact
Not Supported
Support Level
Not 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
2010
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Special project/study: Iowa DNR
TMDL Priority
Tier III
Class BWW1
Aquatic Life - Warm Water Type 1
Not Supported
Support Level
Not Supported
Impairment Code
5b - Biological impairment or pollutant-caused fish kill - unknown source. No administrative action.
Cause Magnitude
Moderate
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2004
Impairment Rationale
Loss of >50% of native mussel species
Data Source
Special project/study
TMDL Priority
Tier IV
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 “not supported” (IR 5p) due to levels of indicator bacteria (E. coli ) that exceed Iowa’s geometric mean criterion. The source of data for this assessment is IDNR bacterial monitoring during the recreation seasons of 2012 through 2013 at STORET station 15310001 approximately 5 miles east of Cascade. The Class B(WW1) aquatic life uses remain assessed (evaluated) as "not supported" (IR 5b) based on information from the report "Statewide Assessment of Freshwater Mussels (Bivalva, Unionidae) in Iowa Streams" by Arbuckle et al. (2000). As part of this study, sampling results from 1998 and 1999 (Arbuckle et al. 2000) were compared to results from stream sites surveyed in 1984 and 1985 by Frest (1987). On a statewide basis, this comparison showed sharp declines in the numbers of mussel species ("species richness") in Iowa streams and rivers from the mid-1980s to the late 1990s. Fish consumption uses remain "not assessed" due to the lack of fish contaminant monitoring in this stream segment.

Assessment Explanation

The Class A1 (primary contact recreation) uses remain assessed (monitored) as “not supported” based on results of IDNR bacteria monitoring in 2012 and 2013.  The geometric means of indicator bacteria (E. coli ) in the 14 samples collected during the recreational seasons of 2012 and 2013 at station 15310001 were as follows:  the 2012 geometric mean was 717 orgs/100 ml, and the 2013 geometric mean was 4,404 orgs/100 ml.  Both geometric means exceed the Class A1 criterion of 126 orgs/100 ml.  Thirteen of the 14 samples (93%) exceeded the Class A1 single-sample maximum criterion 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 are "not supported" (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.” 

For purposes of Section 303(d) listing, the assessment of the Class B(WW1) aquatic life uses remains based on the percent change in the number of species of freshwater mussels found in the 1984-85 survey versus the 1998-99 survey.  For stream segments having four or more species reported for the 1984-95 survey, results of this comparison were used by staff of the Iowa DNR Water Quality Bureau to assess the degree to which the aquatic life uses of the sampled stream segments are supported.  Greater than a 50% decline in species richness from the 1984-85 to the 1998-99 period suggests an impairment of the aquatic life uses.  Species richness of freshwater mussels at the two sample sites in this segment of Whitewater Creek was 8 and 3, respectively, in the 1984-85 period (average of 5 species) and was zero at both sites  in the 1998-99 period for an average percent change of minus 100%.  Based on these results, the aquatic life uses are assessed (monitored) as “not supported.”  As presented by Arbuckle et al.  (2000), the potential causes of declines in species richness of Iowa's freshwater mussels include siltation, destabilization of stream substrate, stream flow instability, and high instream levels of nutrients (phosphorus and nitrogen).  Their study also suggested the importance of stream shading provided by riparian vegetation to mussel species richness. 

Because these data are now considered too old (greater than five years) to accurately characterize current water quality conditions, the assessment category is considered “evaluated” (indicating an assessment with relatively lower confidence) as opposed to "monitored" (indicating an assessment with relatively higher confidence).  Despite this change in assessment type, this waterbody remains in IR Category 5b. 

Previous assessments of the aquatic life uses of this stream segment were based on occurrence of a fish kill in June 2011.  The kill was attributed to runoff of animal waste.  Iowa DNR follow-up monitoring in October 2013 showed that the fish community in this stream segment was similar to other non-fish kill-affected streams in this ecoregion.  Thus, the fish kill-related impairment of the designated aquatic life uses was moved from IR Category 4d (impaired but TMDL not required) to IR Category 3a (not assessed) for the 2014 Integrated Reporting cycle.  

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

Monitoring and Methods
Assessment Key Dates
9/30/1984
Biological Monitoring
9/30/1999
Biological Monitoring
6/19/2011
Fish Kill
10/8/2013
Biological Monitoring
5/29/2012
Fixed Monitoring Start Date
8/19/2013
Fixed Monitoring End Date
Methods
120
Surveys of fish and game biologists/other professionals
140
Incidence of spills and/or fish kills
320
Benthic macroinvertebrate surveys
420
Indicator bacteria monitoring