Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

White Breast Creek IA 04-LDM-1825

from confluence with Brush Cr. (S22 T72N R23W Lucas Co.) to confluence with unnamed tributary in S4 T71N R24W Clarke Co.

Assessment Cycle
2004
Result Period
2000 - 2002
Designations
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 5b
Legacy ADBCode
IA 04-LDM-0210_2
Overall Use Support
Not supporting
Aquatic Life Use Support
Not supporting
Documentation
Assessment Comments

Assessment based on 2002 REMAP data: Fish IBI= 10 (poor), BM-IBI= 35 (fair).

Basis for Assessment

The assessment was based on data collected in 2002 as part of the DNR/UHL REMAP 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 (F-IBI) and a benthic macroinvertebrate index (BM-IBI).   The indexes rank the biological integrity of a stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum).   The 2002 Fish IBI score was 10 (poor) and the BM-IBI score was 35 (fair).  The aquatic life use support was assessed as not supporting (=NS), based on a comparison of the F-IBI and BM-IBI scores with biological assessment criteria established for previous Section 305(b) reports.  The biological assessment criteria were determined from a statistical analysis of data collected at stream ecoregion reference sites from 1994-2001.

As part of the 2002 REMAP sampling project, stream physical habitat assessment found adverse conditions that are thought to contribute to the biological impairment.   These include, bank instability, excessive silt deposition, lack of instream cover, stream channelization and incision.   Stream temperature exceeded 36C (97F) during continuous d.o.  and temperature monitoring in June 2002.   Channel alterations resulting in wide, shallow, and sluggish stream flow conditions probably contribute to elevated stream temperature.

Monitoring and Methods
Assessment Key Dates
9/24/2002 Biological Monitoring
Methods
220 Non-fixed station physical/chemical monitoring (conventional pollutant only)
315 Regional reference site approach
320 Benthic macroinvertebrate surveys
330 Fish surveys
380 Quan. measurements of instream parms-- channel morphology-- floodplain-- 1-2 seasons-- by prof
Monitoring Levels
Biological 4
Habitat 4
Physical Chemistry 1
Toxic 0
Pathogen Indicators 0
Other Health Indicators 0
Other Aquatic Life Indicators 0
# of Bio Sites 1
BioIntegrity Fair
Causes and Sources of Impairment
Causes Use Support Cause Magnitude Sources Source Magnitude
Other habitat alterations Aquatic Life Support High
  • Bank or Shoreline Modification/Destabilization
  • Channelization
  • Hydromodification
  • High
  • High
  • High
Siltation Aquatic Life Support High
  • Agriculture
  • Bank or Shoreline Modification/Destabilization
  • Channelization
  • Hydromodification
  • High
  • High
  • High
  • High