Iowa DNR
ADBNet

Water Quality Assessments

Impaired Waters List

Yellow River IA 01-YEL-434

mouth (S34 T96N R3W Allamakee Co.) to County Road X-26 bridge in S24 T96N R5W Allamakee Co.

Assessment Cycle
2002
Result Period
1998 - 2000
Designations
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 0
Legacy ADBCode
IA 01-YEL-0070_0
Overall Use Support
Not supporting
Aquatic Life Use Support
Threatened
Fish Consumption
Not assessed
Primary Contact Recreation
Not supporting
Documentation
Assessment Comments

Assessment based on results of (1) 1998 DNR Biocriteria sampling: Fish IBI= 63(good), BM-IBI= 67(good), (2) DNR monthly WQ monitoring at Volney, and (3) WQ monitoring at Sny Magill / Bloody run project site near mouth.

Basis for Assessment

SUMMARY:  Class A (primary contact recreation) uses were assessed as "not supported."  Class B(WW) aquatic life uses were assessed as "fully supported/threatened."  Fish consumption uses remain were not assessed.   The sources of data used for this assessment include results of DNR monthly ambient water quality monitoring conducted on the Yellow River near Volney during the 2000-2001 biennial period (October 1999 through September 2001).   EXPLANATION:  The Class A (primary contact recreation) uses were assessed as "not supported."  Of the 15 samples from this station analyzed for indicator bacteria (fecal coliforms) during summers of 2000 and 2001, three samples were collected during conditions of high river flow.   These high flows resulted in monitoring at river discharges that exceeded the long-term monthly average flow plus one standard deviation of this average (flow statistics from Fischer et al.  1990).   For purposes of Section 305(b) assessments only, DNR uses the long-term average monthly flow plus one standard deviation of this average to identify river flows that are materially affected by surface runoff.   According to the Iowa Water Quality Standards (IAC 1990:8), the water quality criterion for fecal coliform bacteria (200 orgs/100 ml) does not apply "when the waters are materially affected by surface runoff."  The geometric mean of fecal coliform bacteria in the twelve non-runoff-affected samples was 259 orgs/100 ml; four of the twelve samples (33%) exceeded the EPA-recommended single-sample maximum value of 400 orgs/100 ml.   The geometric mean (259 orgs/100 ml) is above the state water quality criterion of 200 orgs/100 ml.   According to U.S.  EPA guidelines for Section 305(b) reporting, if the geometric mean is greater than 200 orgs/100ml the primary contact crecation uses are "not supported" (see pgs 3-33 to 3-35of U.S.  EPA 1997b).   Thus, the Class A (primary contact recreation) uses were assessed as "not supported" for the 2000-2001 biennial period.   Class B(WW) aquatic life uses were assessed as "fully supported/threatened [no declining trend]" due to the occurrence of one violation of the chronic water quality criterion for ammonia-nitrogen in one of the 24 samples collected during the biennial period (this violation occurred on March 21, 2000).   According to U.S.  EPA guidelines for Section 305(b) water quality assessments (U.S.  EPA 1997b, page 3-18), however, one violation of a water quality criterion for a toxic pollutant in an abundant data set (at least 10 samples over at three-year period) set does not indicate an impairment of aquatic life uses.   No violations of state water quality criteria occurred for pH, or dissolved oxygen in the 24 samples during the 2000-2001 biennial period.   In addition, no violations of Class B(WW) chronic criteria occurred in the four samples analyzed for toxic metals or in the seven samples analyzed for pesticides during the biennial period.   The fish consumption uses were not assessed due to the lack of fish contaminant monitoring in this river reach.

Monitoring and Methods
Assessment Key Dates
9/12/2001 Fixed Monitoring End Date
10/7/1999 Fixed Monitoring Start Date
Methods
220 Non-fixed station physical/chemical monitoring (conventional pollutant only)
240 Non-fixed station physical/chemical (conventional + toxicants)
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
420 Water column surveys (e.g. fecal coliform)
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 Good
Causes and Sources of Impairment
Causes Use Support Cause Magnitude Sources Source Magnitude
Pathogens Overall Use Support High
  • Source Unknown
  • High
Pathogens Primary Contact Recreation High
  • Source Unknown
  • High