Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Cedar River IA 02-CED-479

from Rock Cr. nr Orchard (S24 T97N R17W Floyd Co.) to Iowa / Minnesota state line (S8 T100N R18W Mitchell Co.)

Assessment Cycle
2018
Release Status
Final
Data Collection Period
Overall IR Category
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Unknown
Created
7/16/2019 2:26:49 PM
Updated
7/16/2019 2:30:27 PM
Assessment conducted in accordance with Iowa's 2018 IR methodology
Use Support
Class A1
Recreation
Primary contact
Partially Supported
Impairments
Support Level
Partially Supported
Impairment Code
4a - Pollutant-caused impairment. TMDL has been completed.
Cause Magnitude
Slight
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2006
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Special project/study
Class BWW1
Aquatic Life
Warm Water Type 1
Fully Supported
Class HH
Human Health
Partially Supported
Impairments
Support Level
Partially Supported
Impairment Code
5a - Pollutant-caused impairment. TMDL needed.
Cause Magnitude
Slight
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2006
Impairment Rationale
Fish consumption advisory in effect: no more than 1 meal/week
Data Source
Fish contaminant monitoring: Iowa DNR
TMDL Priority
Tier IV
General Use
General Use water
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class A1 (primary contact recreation) uses are assessed (monitored) as "partially supported" (IR 4a) based on levels of indicator bacteria (E. coli) that slightly exceed Class A1 criteria.  The Class B(WW1) aquatic life uses are assessed (evaluated) as "fully supported" (IR 2a) based on results of the IDNR/SHL biological monitoring in 2006 and on results of water quality monitoring at three station during the 2012-2014 period.  The fish consumption uses remain assessed (monitored) as "partially supporting" (IR 5a) based on results of fish contaminant monitoring in 2001, 2005, 2007 and 2008 and the issuance of a "one meal per week" fish consumption advisory in 2006.  Sources of information for this assessment include (1) results of monitoring from IDNR/SHL stations monitored from 2014 to 2016 as part of the Cedar River/Mitchell County project at IA/MN state line (STORET No. 15660010); (2) results of monitoring from May to August 2013 at USGS station 05457520, (3) results of a 1998-99 statewide assessment of freshwater mussels in Iowa streams (Arbuckle et al. 2000), (4) results of an IDNR mussel survey in July 2012, (5) results of U.S. EPA/IDNR fish contaminant (RAFT) monitoring near Osage in 2001, 2005, 2007, 2008, and 2009, and (5) 2006 IDNR/SHL stream REMAP biological sampling at two sites: near St. Ansgar and near Osage. 

Assessment Explanation

[Note: A TMDL for indicator bacteria in this segment of Cedar River was prepared and approved by EPA in February 2010. The approval of this TMDL moves the bacterial impairment for this segment from Iowa's list of Section 303(d) waters (Category 5a of the Integrated Report) to IR Category 4a (impaired; TMDL not required). Because, however, the impairment due to the existence of the mercury-related fish consumption advisory was not covered by this TMDL, this segment of the Cedar River remains in Category 5a (impaired and TMDL required) of Iowa's Integrated Report.]

The Class A1 (primary contact recreation) uses are assessed (monitored) as "partially supported" based on levels of indicator bacteria that exceeded state water quality criteria. The geometric means of indicator bacteria (E. coli) in the 18 samples collected during the recreational seasons of 2014 through 2016 at Iowa DNR station 15660010 (Cedar River at State Line St.) were as follows: the 2014 geometric mean was 86 orgs/100 ml, the 2015 geometric mean was 356 orgs/100 ml, and the 2016 geometric mean was 120 orgs/100 ml. One of the three recreation season geometric means exceeded the Class A1 geometric mean criterion of 126 orgs/100 ml. Four of the combined 18 samples (22%) exceeded Iowa’s Class A1 single-sample maximum criterion of 235 orgs/100 ml. According to U.S. EPA guidelines for Section 305(b) reporting and Iowa DNR’s assessment/listing methodology, if the geometric mean is greater than 126 orgs/100 ml., the primary contact recreation uses should be assessed as "impaired" (see pgs 3-33 to 3-35 of U.S. EPA 1997b). Thus, because at least one recreation season geometric mean exceeded criteria for Class A1 uses, these uses are assessed as "partially supported."

Results of DNR surveys of freshwater mussels at one site in this assessment segment suggest that the biological impairment based on the apparent decline of freshwater mussels no longer exists. The original impairment was based on a comparison of sampling results from 1998 and 1999 (Arbuckle et al. 2000) to results from stream sites surveyed in 1984 and 1985 by Frest (1987). Impairment was based on the percent change in the number of species of freshwater mussels found in the 1984-85 survey versus the 1998-99 survey. Greater than a 50% decline in species richness from the 1984-85 to the 1998-99 period suggested an impairment of the aquatic life uses. Based on DNR’s assessment approach, the degree of decline (100%) in the number of freshwater mussel species in this segment suggested “partial support” (impairment) of the Class B(WW) aquatic life uses for purposes of both Section 303(d) listing and 303(d) reporting. Results of the DNR's surveys in 2012, however, show recovery in the number of freshwater mussel species at the site used to identify the original impairment. Twelve species were found in this segment in 1984 with eight species found in July 2012. Because more than 50 percent of the species present in 1984 were found in the 2012 survey, this impairment is moved from Category 5b of Iowa's Integrated Report to IR Category 3a (insufficient information to develop an assessment of support of uses).


The 2006 DNR/SHL stream REMAP biological sampling at two sites also suggested (evaluated) "full support" of the Class B(WW1) aquatic life uses. This evaluated biological assessment was based on data collected in 2006 as part of the DNR/SHL stream REMAP project. A series of biological metrics that 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 collected in the stream sampling reach. The biological metrics were combined to make a fish community index of biotic integrity (FIBI) and a benthic macroinvertebrate index (BMIBI). The indexes rank the biological integrity of a stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum). The 2006 FIBI scores were 46 (fair) and 74 (excellent) and the BMIBI scores were 76 (excellent), 75 (good). The aquatic life use support was assessed (evaluated) as fully supporting (=FS), based on a comparison of the FIBI and BMIBI scores with biological impairment criteria (BIC) established from a statistical analysis of data collected at stream ecoregion reference sites from 1994-2008. The non-riffle habitat FIBI BIC for this ecoregion is 44 and the natural substrate BMIBI BIC for this ecoregion is 70. This segment passed the FIBI BIC 2/2 times and passed the BMIBI BIC 2/2 times in 2006. This assessment is considered evaluated because the drainage areas (675 & 862 mi2) above the sampling sites were greater than the maximum limit (500 mi2) that was used to calibrate the Iowa wadeable stream impairment criteria. Even though this site passed both the FIBI and BMIBI BICs, it is uncertain as to whether or not this segment is meeting the aquatic life criteria becausethe sites used for the assessmentdon’t fall in the calibrated watershed size.

Results of chemical/physical water quality monitoring at Iowa DNR station 15660010 (Cedar River at State Line St.) suggest “full support” of the aquatic life uses. Monitoring showed no violations of Class B(WW1) water quality criteria for 5 Dissolved Oxygen samples (minimum = 8 mg/L), 11 pH samples (range = 7.4 to 8.6), or 11 Temperature samples (maximum = 20.5°C) occurred during monitoring from July 2015 to October 2016.According to U.S. EPA guidelines for Section 305(b) water quality assessments (U.S. EPA 1997b, page 3-17), the EPA guidelines allow up to 10% violations of these conventional parameters before impairment of water quality is indicated. Thus, these results thus suggest “full support” of the Class B(WW1) aquatic life uses.

Fish consumption uses remain assessed (monitored) as “partially supported” based on results of U.S.EPA/DNR fish contaminant (RAFT) monitoring near Osage in 2001, 2005, 2007, 2008, and 2009. The existence of, or potential for, a fish consumption advisory is the basis for Section 305(b) assessments of the degree to which Iowa’s lakes and rivers support their fish consumption uses. The level of mercury in the composite sample of smallmouth bass fillets (0.305 ppm) from the 2001 RAFT sampling slightly exceeded the DNR/IDPH trigger level of 0.30 ppm for a one meal per week consumption advisory (this levels is well below the “do not eat” trigger level for mercury of 1.0 ppm). According to the DNR/IDPH advisory protocol, if two consecutive samplings show that contaminant levels are above the trigger level in fillet samples, issuance of a consumption advisory is justified. Because the level of mercury in composite sample of walleye fillets from the 2005 sampling (0.33 ppm) also exceeded this advisory trigger level, issuance of a fish consumption advisory is justified. This advisory was issued by DNR and IDPH in January 2006 and covers the reach of the Cedar River from the Highway 218 bridge at Floyd, IA upriver to the Iowa/Minnesota state line. According to DNR’s assessment methodology, the existence of a consumption advisory indicates that fish consumption uses should be assessed as “partially supported.”


Follow-up sampling was conducted in 2007, 2008, and 2009 to better assess the amount of mercury in fish in this river segment. The composite samples of smallmouth bass fillets in 2007 and 2008 had low levels of mercury (2007: 0.219 ppm, 2008: 0.19 ppm). These levels were below the advisory trigger level (0.30 ppm). Based on DNR's assessment methodology two consecutive samples with levels below the advisory trigger level are necessary to suggest "full support" of the fish consumption uses. While this is the case for this segment of the Cedar River, there were no samples of walleye collected, therefore it is not known if levels of mercury in walleye are also below the advisory trigger level. The composite samples of smallmouth bass fillets in 2009 had a level of mercury (0.351 ppm) that again exceeded the advisory trigger level. Therefore the fish consumption advisory will remain and the fish consumption uses will remain assessed as "partially supported". Additional follow-up monitoring will be conducted to determine if the levels of mercury in walleye are also below advisory trigger levels.

Monitoring and Methods
Assessment Key Dates
9/30/1999
Biological Monitoring
9/1/2001
Fish Tissue Monitoring
9/14/2005
Fish Tissue Monitoring
7/5/2006
Biological Monitoring
8/11/2008
Fish Tissue Monitoring
8/6/2009
Fish Tissue Monitoring
4/22/2014
Fixed Monitoring Start Date
10/10/2016
Fixed Monitoring End Date
8/8/2007
Fish Tissue Monitoring
Methods
120
Surveys of fish and game biologists/other professionals
220
Non-fixed station physical/chemical monitoring (conventional pollutant only)
230
Fixed station physical/chemical (conventional plus toxic pollutants)
260
Fish tissue analysis
315
Regional reference site approach
320
Benthic macroinvertebrate surveys
330
Fish surveys
380
Quantitative physical habitat assessment
420
Indicator bacteria monitoring