Iowa DNR
Iowa DNR
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Water Quality Assessments
Impaired Waters List

South Fork Chariton River IA 05-CHA-1328

from confluence with Ninemile Cr. (S4 T69N R22W Wayne Co.) to outfall of Bob White Lake in S4 T68N R22W Wayne Co.

Assessment Cycle
2004
Result Period
2000 - 2002
Designations
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 5a
Legacy ADBCode
IA 05-CHA-0060_2
Overall Use Support
Partial
Aquatic Life Use Support
Partial
Documentation
Assessment Comments

Assessment is based on results of ambient water quality monitoring conducted from 2000-02 as part of the Rathbun Lake Water Quality Project and on 1999-2002 Fisheries data: Fish IBI average (n=4) = 19 (poor).

Basis for Assessment

SUMMARY:  The Class B(LR) aquatic life uses remain assessed (monitored) as "partially supported" due to levels of dissolved oxygen that violate Iowa water quality standards.   The assessment of support of the Class B(LR) uses is based on results of water quality monitoring conducted in 2000, 2001, and 2002 on the South Fork Chariton River near Cambria (station RA-35) by Iowa State University under contract with the U.S.  Army Corps of Engineers-Kansas City District as part of the Rathbun Water Quality Project.    

EXPLANATION:  Although none of the 26 samples violated Class B(LR) criteria for ammonia-nitrogen (maximum level = 0.45 mg/l) or for pH, monitoring results for dissolved oxygen continue to suggest a potentially significant water quality problem.   Three of the 26 samples collected (12%) at station RA-35 in 2000, 2001, and 2002 violated the Class B(LR) water quality criterion for dissolved oxygen; all of these violations occurred in the relatively dry year of 2000 and are as follows:  4.9 mg/l on May 16, 2.6 mg/l on June 13, and 1.8 mg/l on June 27.   According to U.S.  EPA guidelines for Section 305(b) water quality assessments (U.S.  EPA 1997b, page 3-17), if criteria for conventional parameters (e.g., pH, dissolved oxygen and temperature) are exceeded in from 11% to 25% of the samples "partial support" of beneficial uses is indicated.   Thus, the violation frequency of the Class B(LR) criterion for dissolved oxygen (16%) suggests "partial support" of the Class B(LR) aquatic life uses.   Similar to results of monitoring conducted in 1998 and 1999, results from the 2000-2002 period continued to show high levels of nutrient parameters.   While levels of total nitrogen in the South Fork Chariton River and other streams in the Rathbun watershed are relatively low for Iowa, levels of total phosphorus tend to be relatively high.   The 2000-2002 mean and median levels for total phosphorus at Station RA-35 were 0.28 mg/l and 0.25 mg/l, respectively (N=26); the mean and median levels of total nitrogen for this period were 2.1 mg/l and 1.9 mg/l, respectively (N=25).   The Iowa Water Quality Standards does not currently have aquatic life criteria for these nutrient parameters or for other nonpoint source-related parameters (for example, total suspended solids).   The Iowa DNR is, however, participating in a nationwide program, led by U.S.  EPA, for states to develop and adopt surface water criteria for total phosphorus, total nitrogen, chlorophyll, and some measure of turbidity.   Although this river reach is not designated for Class C drinking water uses, the South Fork Chariton River does flow into Rathbun Reservoir which is designated for Class C uses.   Thus, the seasonal elevation of pesticides levels in this stream and other tributaries of Rathbun Reservoir presents a continuing threat to full support of the Class C (drinking water) uses designated for Rathbun Reservoir.   For example, the mean level of atrazine in the 26 samples collected at Station RA-35 in 2000, 2001, and 2002 (3.7 ug/l) exceeded the atrazine MCL of 3.0 ug/l; the maximum levels of 38.1 ug/l of atrazine occurred in the sample collected on June 1, 2001.

The assessment was partially based on data collected in 1999-2002 as part of a DNR Fisheries stream sampling project: Chariton research station.   A series of biological metrics which reflect stream water quality and habitat integrity were calculated from the Fisheries sampling data.   The biological metrics are based on the numbers and types of 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).   The index ranks the biological integrity of a stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum).   The 1999-2002 evaluated Fish IBI average score (n=4) was 19 (poor).   The aquatic life use support was assessed (evaluated) as Not Supporting (=NS), based on a comparison of the F-IBI score 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.

Monitoring and Methods
Assessment Key Dates
12/11/2002 Fixed Monitoring End Date
7/19/2002 Biological Monitoring
7/16/2001 Biological Monitoring
7/31/2000 Biological Monitoring
3/28/2000 Fixed Monitoring Start Date
9/13/1999 Biological Monitoring
Methods
240 Non-fixed station physical/chemical (conventional + toxicants)
315 Regional reference site approach
330 Fish surveys
Monitoring Levels
Biological 3
Habitat 0
Physical Chemistry 3
Toxic 0
Pathogen Indicators 0
Other Health Indicators 0
Other Aquatic Life Indicators 0
# of Bio Sites 2
BioIntegrity Poor
Causes and Sources of Impairment
Causes Use Support Cause Magnitude Sources Source Magnitude
Organic enrichment/Low DO Aquatic Life Support Moderate
  • Source Unknown
  • Moderate