Iowa DNR
Iowa DNR
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Water Quality Assessments
Impaired Waters List

Little Cedar River IA 02-CED-574

mouth (S20 T94N R14W Chickasaw Co.) to the Chickasaw/Floyd county line at W line S6 T95N R14W Chickasaw Co.

Assessment Cycle
2006
Result Period
2002 - 2004
Designations
Class B(WW)
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 1
Legacy ADBCode
IA 02-CED-0470_1
Overall Use Support
Fully
Aquatic Life Use Support
Fully
Fish Consumption
Fully
Documentation
Assessment Comments

Assessment is based on results of (1) IDNR/UHL ambient monitoring conducted from 2002-04 in support of TMDL development and (2) biological monitoring conducted by IDNR and UHL in 1995 and (3) EPA/IDNR fish contaminant (RAFT) monitoring in 2003.

Basis for Assessment

SUMMARY:  The Class B(WW) aquatic life uses are assessed (monitored) as "fully supported" based on results TMDL-related water quality monitoring from 2002 through 2004.   Fish consumption uses are assessed (monitored) as “fully supported” based on results of fish contaminant monitoring in 2003.   The sources of data for this assessment are the results of (1) monthly monitoring conducted by IDNR and UHL at one location near Ionia (STORET station 11190001 (station 69)) from January 2002 through December 2004 as part of monitoring in support of TMDL development and (2) U.S.  EPA/IDNR fish contaminant (RAFT) monitoring in 2003.  

EXPLANATION:  The assessment of the Class B(WW) uses for the current (2002-2004) assessment period ("fully supported") is based on results of TMDL-related monitoring near Ionia from 2002 through 2004 that showed no violations of Class B(WW) criteria for dissolved oxygen or pH in the 41 samples collected, or for ammonia-nitrogen in the 32 samples collected and analyzed.   The parameter coverage at this station is somewhat limited (i.e., no analysis for toxic metals or pesticides).   This assessment is consistent with previous assessments of aquatic life uses (“fully supported”) based on results of IDNR/UHL biocriteria sampling in 1995 and on results of IDNR stream use assessments in 1995 (see assessment developed for the 2000 report).  

Fish consumption uses were assessed (monitored) as “fully supported” based on results of U.S.EPA/IDNR fish contaminant (RAFT) monitoring at Chickasaw Park in 2003.   The existence of, or potential for, a fish consumption advisory is the basis for Section 305(b) assessments of support of fish consumption uses in Iowa’s rivers and lakes.   Prior to 2006, IDNR used action levels published by the U.S Food and Drug Administration to determine whether consumption advisories should be issued for fish caught as part of recreational fishing in Iowa.   In an effort to make Iowa’s consumption more compatible with the various protocols used by adjacent states, the Iowa Department of Public Health, in cooperation with Iowa DNR, developed a risk-based advisory protocol.   This protocol went into effect in January 2006 (see http://www.iowadnr.gov/fish/news/consump.html for more information on Iowa’s revised fish consumption advisory protocol).   Because the revised (2006) protocol is more restrictive than the previous protocol based on FDA action levels; fish contaminant data that previously suggested “full support” may now suggest impairment of the fish consumption uses.  

Although this scenario does not apply to the fish contaminant data generated from the 2003 RAFT sampling conducted in this assessment segment, levels of contaminant are sufficiently high for concern and justify follow-up monitoring.   The levels of at least one contaminant from past monitoring now exceeds one or more advisory trigger levels, thus suggesting the need for additional (follow-up) monitoring to determine whether a consumption advisory should be issued.  

The composite samples of fillets from common carp and smallmouth bass had generally low levels of contaminants.   Levels of primary contaminants in the composite sample of carp fillets were as follows: mercury: 0.097 ppm; total PCBs: 0.09 ppm; and technical chlordane: < 0.03 ppm.   Levels of primary contaminants in the composite sample of smallmouth bass fillets were as follows: mercury: 0.225 ppm; total PCBs: 0.09 ppm; and technical chlordane: < 0.03 ppm.   Although assessed as “fully supported” for this reporting cycle, the level of at least one contaminant does, however, now exceed one or more advisory trigger levels:  the level of mercury in the sample of smallmouth bass fillets (0.225 ppm) slightly exceeds the one meal per week trigger level of 0.20 ppm.   According to the IDNR/IDPH advisory protocol, this single result neither warrants issuance of an advisory nor indicates impairment of the fish consumption uses:  two consecutive samplings that show contaminant levels are above the trigger level in fillet samples are needed to justify issuance of an advisory.   But, this elevated level does indicate a concern and the need to conduct additional monitoring to better define contaminant levels in fish from this river segment.   Thus, follow-up monitoring will be conducted in 2006 to better determine (1) levels of mercury in the edible portions (fillets) of fish in this river segment and (2) whether a one-meal-per-week consumption advisory needs to be issued.

Monitoring and Methods
Assessment Key Dates
12/8/2004 Fixed Monitoring End Date
7/30/2003 Fish Tissue Monitoring
1/8/2002 Fixed Monitoring Start Date
10/3/1995 Biological Monitoring
8/1/1995 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
260 Fish tissue analysis
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 0
BioIntegrity N/A
Causes and Sources of Impairment
Causes Use Support Cause Magnitude Sources Source Magnitude
Mercury Fish Consumption Not Impairing
  • Source Unknown
  • Not Impairing