Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Mill Creek IA 06-LSR-1615

mouth (S14 T92N R40W Cherokee Co.) to confluence with Whisky Cr. at east line S29 T94N R41W O'Brien Co.

Assessment Cycle
2004
Result Period
2000 - 2002
Designations
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 5b
Legacy ADBCode
IA 06-LSR-0170_0
Overall Use Support
Partial
Aquatic Life Use Support
Partial
Documentation
Assessment Comments

Assessment is based on 2002 DNR/UHL REMAP data: Fish IBI= 36 (fair), BM-IBI= 43 (fair) and on 1998 DNR/UHL biocriteria data: Fish IBI=43 (fair), BM-IBI=75 (good).

Basis for Assessment

SUMMARY:  For the 2004 reporting period, the assessment of Class B(LR) aquatic life uses was downgraded to "partially supporting" (PS) from "fully supported / threatened" (FS/T) for the 2002 reporting period.   The assessment segment includes data collected in 1998 and 2002 as part of the DNR/UHL stream biocriteria and REMAP projects.  The 1998 Fish IBI score was 43 (fair) and the BM-IBI score was 75 (good).   The 2002 Fish IBI score was 36 (fair) and the BM-IBI score was 43 (fair).   Relying on the more recent (2002) data, the aquatic life use support was assessed as partially supporting (=PS).   The assessment was 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.        

EXPLANATION:  The 2004 assessment relies on more recent (2002) sample data collected from a different (upstream) area of the assessment segment.   This area exhibited degraded physical habitat and water quality conditions compared with stream reference site conditions.   Elevated levels of total phosphorus, TSS, and turbidity were found in  two summer base flow water samples.   Seston (water column) chlorophyll a, and high estimated rates of gross primary production and community respiration were indicative of a nutrient/organically-enriched  environment.   Several types of physical habitat alteration were evident, including removal (grazing) of riparian vegetation,  bank destabilization, channel widening, and excessive sediment deposition.

Monitoring and Methods
Assessment Key Dates
8/21/2002 Biological Monitoring
10/7/1998 Biological Monitoring
Methods
320 Benthic macroinvertebrate surveys
330 Fish surveys
380 Quan. measurements of instream parms-- channel morphology-- floodplain-- 1-2 seasons-- by prof
220 Non-fixed station physical/chemical monitoring (conventional pollutant only)
315 Regional reference site approach
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 Good
Causes and Sources of Impairment
Causes Use Support Cause Magnitude Sources Source Magnitude
Organic enrichment/Low DO Aquatic Life Support Moderate
  • Agriculture
  • Pasture grazing - Riparian
  • Source Unknown
  • Moderate
  • Moderate
  • Moderate
Other habitat alterations Aquatic Life Support Moderate
  • Agriculture
  • Bank or Shoreline Modification/Destabilization
  • Habitat Modification (other than Hydromodification)
  • Hydromodification
  • Pasture grazing - Riparian
  • Removal of Riparian Vegetation
  • Moderate
  • Moderate
  • Moderate
  • Moderate
  • Moderate
  • Moderate
Siltation Aquatic Life Support Moderate
  • Agriculture
  • Pasture grazing - Riparian
  • Moderate
  • Moderate