Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Cedar River IA 02-CED-472

from W. Fk. Cedar R. (S4 T90N R14W Black Hawk Co.) to lowhead dam at Waverly in NW 1/4 S2 T91N R14W Bremer Co.

Cycle
2018
Release Status
Final
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Unknown
Created
5/21/2019 6:55:12 AM
Updated
7/11/2019 11:35:35 AM
Use Support
Class A1
Recreation - Primary contact
Partially Supported
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
2008
Impairment Rationale
Single-sample maximum criterion exceeded in significantly > 10% of samples
Data Source
Ambient monitoring: Iowa DNR-rivers
TMDL Priority
Tier III
Class BWW1
Aquatic Life - Warm Water Type 1
WINOFI
Impairment Code
3b-u - Use potentially biologically impaired based on uncalibrated IBI metrics.
Cause Magnitude
Slight
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
Low
Cycle Added
2014
Impairment Rationale
Low Biotic Index
Data Source
Biological monitoring: Iowa DNR WQMA
Class HH
Human Health -
Not Assessed
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" based on results of ambient monitoring for indicator bacteria during recreational seasons of the previous (2008-2010) assessment period:  results of monitoring during the current (2010-2012) assessment period do not suggest a bacteria impairment.  The Class B(WW1) aquatic life uses are assessed (evaluated) as "partially supported" based on results of biological sampling conducted in 2007 and 2012-2014.  Fish consumption uses remain "not assessed" due to the lack of fish contaminant monitoring in this river segment.  The source of data for this assessment are the: (1) results of monthly monitoring from 2014 through 2016 at the DNR ambient monthly monitoring station located near Janesville in Bremer County (station 10090001), (2) DNR/SHL biological sampling conducted near Janesville and (3) DNR Fisheries Bureau sampling conducted downstream of Waverly. 

Assessment Explanation

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 24 samples collected during the recreational seasons of 2014 through 2016 at the DNR ambient monitoring station (10090001) upstream near Janesville were as follows: the 2014 geometric mean was 105 orgs/100 ml, the 2015 geometric mean was 45 orgs/100 ml, and the 2016 geometric mean was 137 orgs/100 ml. One of the three recreation season geometric means exceeded the Class A1 geometric mean criterion of 126 orgs/100 ml. Three of the combined 24 samples (12%) 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 chemical/physical water quality monitoring at the DNR ambient monitoring station (10090001) upstream near Janesville also/ however/ suggest “full support” of the aquatic life uses. Monitoring showedno violations of Class B(WW1) water quality criteria for 35 Ammonia samples (maximum = 0.5 mg/L), 36 Dissolved Oxygen samples (minimum = 7.7 mg/L), 35 pH samples (range = 7.6 to 8.8), 36 Temperature samples (maximum = 25.6°C), 36 Chloride samples (maximum = 35 mg/L), or 36 Sulfate samples (maximum = 34 mg/L) occurred during monitoring from January 2014 to December 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.

In contrast to the water quality aquatic life assessment, the aquatic life assessment based on biological sampling suggests the aquatic life uses remain "partially supporting". This evaluated biological assessment was based on data collected in 2007 and 2012-2014 as part of the DNR/SHL stream nutrient sampling project and on data collected in 2007 as part of sampling conducted by the DNR Fisheries Bureau. A series of biological metrics that reflect stream water quality and habitat integrity were calculated from the biological sampling data. The biological metrics are based on the numbers and types of benthic macroinvertebrate taxa collected in the stream sampling reach. The biological metrics were combined a benthic macroinvertebrate index (BMIBI). The index rank the biological integrity of a stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum). The 2007 FIBI score was 74 (excellent). The 2012-2014 BMIBI scores were 48, 52, 53, 54 (all fair) and 59, 65 (both good). The aquatic life use support was assessed (evaluated) as partially supporting (=PS), based on a comparison of the BMIBI scores with biological impairment criteria (BIC) established from a statistical analysis of biological data collected at stream ecoregion reference sites from 1994-2008. The artificial substrate BMIBI BIC for this ecoregion is 52 and the natural substrate BMIBI BIC is 70. This assessment is considered evaluated because the drainage area (1549 and 1671 mi2) above the sampling sites was greater than the maximum limit (500 mi2) that was used to calibrate the Iowa wadeable stream impairment criteria. The segment passed the 2013 and 2014 artificial substrate BMIBI BIC and failed the BMIBI BICs on the other four samples.

Even though this site passed the FIBI BIC in 2007 and failed the BMIBI BIC (2/6 times) in the last five years, it is uncertain as to whether or not this segment is meeting the aquatic life criteria because the sites used for the assessmentdon’t fall in the calibrated watershed size. According to DNR’s assessment/listing methodology, impairments based on “evaluated” assessments are of lesser confidence and are thus not appropriate for Section 303(d) listing (Category 5 of the Integrated Report). DNR does, however, consider these impairments as appropriate for listing under either Category 2b or 3b of the Integrated Report (waters potentially impaired and in need of further investigation).

Fish consumption uses remain not assessed due to the lack of recent fish tissue monitoring in this river segment.

Monitoring and Methods
Assessment Key Dates
8/6/2012
Biological Monitoring
1/7/2014
Fixed Monitoring Start Date
12/6/2016
Fixed Monitoring End Date
9/20/2007
Biological Monitoring
9/3/2013
Biological Monitoring
9/9/2014
Biological Monitoring
Methods
150
Monitoring data more than 5 years old
230
Fixed station physical/chemical (conventional plus toxic pollutants)
315
Regional reference site approach
320
Benthic macroinvertebrate surveys
330
Fish surveys
420
Indicator bacteria monitoring