Iowa DNR
ADBNet

Water Quality Assessments

Impaired Waters List

Old Mans Creek IA 02-IOW-686

from confluence with unnamed tributary (N line S1 T78N R7W Johnson Co.) to confluence with unnamed tributary in NE 1/4 S4 T78N R8W Johnson Co.

Assessment Cycle
2002
Result Period
1998 - 2000
Designations
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 0
Legacy ADBCode
IA 02-IOW-0150_2
Overall Use Support
Threatened
Aquatic Life Use Support
Threatened
Documentation
Assessment Comments

Assessment based on results of IDNR ambient monitoring in 2000 and 2001. Assessment based on 2000 biocriteria data: Fish IBI= 28 (fair), BM-IBI= 54 (fair).

Basis for Assessment

[NOTE:  For the 2002 report, the previous waterbody segment for Old Mans Creek (IA 02-IOW-0150-0), which extended 40 miles from the its mouth to its confluence with Hog Run in Iowa County, was split into four subsegments:  (1) mouth to unnamed tributary southwest of Iowa city (IA 02-IOW-0150-1), (2) unnamed tributary southwest of Iowa City to unnamed tributary southwest of Cosgrove (IA 02-IOW-0150-2), (3) unnamed tributary southwest of Cosgrove to Convey Creek (IA 02-IOW-0150-3), and (4) Convey Creek to Hog Run, Iowa Co.  (IA 02-IOW-0150-4).   The assessments devleoped for previous Section 305(b) repoting cycles (found in the assessment in formation for segment IA 02-IOW-0150-2) apply to the original 40-mile segment.]

SUMMARY:  The Class B(LR) aquatic life uses remain assessed as "fully supported / threatened."  Fish consumption uses are not assessed.   The assessment of support of the Class B(LR) uses is based on results of monitoring conducted on Old Mans Creek near Iowa City at the Co.Rd.  W62 bridge from October 2000 to September 2001 as part of the IDNR ambient water quality monitoring program.   EXPLANATION:  Results of the IDNR monitoring showed no violations of Class B(LR) water quality criteria in the 12 samples analyzed for pH, dissolved oxygen, and ammonia.   In addition, no violations of Class B(LR) chronic criteria occurred in the 4 samples analyzed for pesticides.   Although the monitoring results for conventional and toxic parameters suggests "full support" of the aquatic life uses, the assessment of "fully supported / threatened" is used due to concerns with results of past biological monitoring (see assessment for the 2000 report).   Additional biological monitoring is needed to better determine the status of the aquatic communities of this stream.   Fish consumption uses are "not assessed because (1) data used for the previous assessment (see 1998 assessment above) are now considered too old (greater than five years) for characterizing current water quality conditions and (2) fish consumption uses are not considered appropriate for Class B(LR) streams.  

The assessment was based on data collected in 2000 as part of the DNR/UHL 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 (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 2000 Fish IBI score was 28 (fair) and the BM-IBI score was 54 (fair).  The aquatic life use support was assessed as fully supported / threatened (=FST), based on a comparison of the F-IBI and BM-IBI scores with biological assessment criteria established specifically for the 2002 Section 305(b) report.  The biological assessment criteria were determined from a statistical analysis of data collected at stream ecoregion reference sites from 1994-2001.

Monitoring and Methods
Assessment Key Dates
9/5/2001 Fixed Monitoring End Date
10/4/2000 Fixed Monitoring Start Date
9/7/2000 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)
230 Fixed station physical/chemical (conventional plus toxic pollutants)
315 Regional reference site approach
Monitoring Levels
Biological 4
Habitat 4
Physical Chemistry 3
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 Overall Use Support Not Impairing
  • Source Unknown
  • Not Impairing
Siltation Overall Use Support Not Impairing
  • Agriculture
  • Bank or Shoreline Modification/Destabilization
  • Channelization
  • Habitat Modification (other than Hydromodification)
  • Hydromodification
  • Not Impairing
  • Not Impairing
  • Not Impairing
  • Not Impairing
  • Not Impairing