Iowa DNR
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Water Quality Assessments

Impaired Waters List

Cedar Creek IA 04-LDM-1053

mouth (S33 T75N R17W Mahaska Co.) to confluence with North Cedar Cr. in S15 T74N R18W Marion Co.

Assessment Cycle
2016
Release Status
Final
Data Collection Period
Overall IR Category
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Unknown
Created
9/30/2016 9:35:38 AM
Updated
10/7/2016 10:17:37 AM
Assessment conducted in accordance with Iowa's 2016 IR methodology
Use Support
Class A1
Partially Supported
Bacteria: Indicator Bacteria- E. coli
Support Level
Partially Supported
Impairment Code
5p - Impairment occurs on a waterbody with a presumptive A1 or B(WW1) use.
Cause Magnitude
Slight
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2008
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Ambient monitoring: Iowa DNR-rivers
TMDL Priority
Tier III
Class BWW1
WINOFI
Biological: low aquatic macroinvertebrate IBI
Support Level
Water in Need of Further Investigation (WINOFI)
Impairment Code
3b-c - Use potentially biologically impaired based on calibrated IBI metrics.
Cause Magnitude
Moderate
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
Not Assessed
General Use
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The presumptive Class A1 (primary contact recreation) uses are assessed (monitored) as "partially supported" (IR 5p) due to levels of indicator bacteria that violate state water quality criteria. The Class B(WW1) aquatic life uses are assessed (evaluated) as "not supported" (IR 3b-c) based on results of IDNR/SHL biological sampling. Fish consumption uses remain "not assessed" (IR 3a) due to the lack of fish contaminant monitoring in this stream segment. The sources of data for this assessment are the results of: (1) IDNR/SHL ambient monthly monitoring during the 2012-2014 assessment period at STORET station 10630002 (formerly station 500680) at the Highway 156 bridge approximately 1.5 miles northwest of Bussey and (2) 2012 IDNR/SHL large river benthic macroinvertebrate sampling conducted near Bussey.

Assessment Explanation

The presumptive Class A1 uses are assessed (monitored) as "partially supported" based on results of ambient monitoring for indicator bacteria (E. coli). The geometric means of indicator bacteria (E. coli) in the 24 samples collected during the recreational seasons of 2010 through 2012 at IDNR station 10630002 near Bussey were as follows: the 2012 geometric mean was 260 orgs/100 ml, the 2013 geometric mean was 144 orgs/100 ml, and the 2014 geometric mean was 464 orgs/100 ml. All three geometric means slightly exceed the Class A1 criterion of 126 orgs/100 ml. Ten of the 24 samples (42%) exceeded the Class A1 single-sample maximum criterion of 235 orgs/100 ml. According to U.S. EPA guidelines for Section 305(b) reporting and IDNR’s assessment/listing methodology, if a recreation season geometric mean exceeds the respective water quality criterion, the 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.”

Based exclusively on the water quality data, the Class B(WW1) aquatic life uses should be assessed (monitored) as "fully supported.” None of the 36 samples collected during the 2012-2014 assessment period at the IDNR/UHL monthly station violated Class B(WW1) water quality criteria for pH or ammonia-nitrogen, temperature, chloride, or sulfate. One of the 36 samples collected (3%) exceeded the Class B(WW1) criterion of 5.0 mg/l for dissolved oxygen (4.8 mg/l). According to U.S. EPA guidelines for Section 305(b) reporting, if more than 10% of samples exceed state criteria for conventional parameters such as dissolved oxygen, the aquatic life uses should be assessed as "impaired" (see pgs 3-33 to 3-35of U.S. EPA 1997b). According to IDNR’s assessment/listing methodology, however, the results from IDNR station 10630002 do not indicate that greater than 10% of the samples exceed the Class B(WW1) criteria for dissolved oxygen. Thus, these results do not suggest impairment of the Class B(WW1) aquatic life uses. Contrary to the biological data (below), these results suggest that the Class B(WW1) aquatic life should be assessed as "fully supported."

In disagreement with the water quality data and assessment for this segment, the biological data suggest that the aquatic life uses in this segment are "not supporting." This evaluated aquatic life assessment was based on data collected in 2012 as part of the IDNR/SHL large river sampling project. A series of biological metrics which 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 to make a benthic macroinvertebrate index (BMIBI). The index ranks the biological integrity of a stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum). The 2012 BMIBI score was 12 (poor). The aquatic life use support was assessed as not supporting (=NS), based on a comparison of the BMIBI score with biological impairment criteria (BIC) established for previous Section 305(b) reports. The BMIBI BIC for this ecoregion is 41. The biological impairment criteria were determined from a statistical analysis of biological data collected at stream ecoregion reference sites from 1994-2008. This assessment is considered "evaluated" because there were not two or more samples collected in multiple years from 2010-2014. According to IDNR’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). IDNR 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 contaminant monitoring in this stream segment.

Monitoring and Methods
Assessment Key Dates
8/27/2012 Biological Monitoring
1/3/2012 Fixed Monitoring Start Date
12/3/2014 Fixed Monitoring End Date
Methods
230 Fixed station physical/chemical (conventional plus toxic pollutants)
315 Regional reference site approach
320 Benthic macroinvertebrate surveys
420 Indicator bacteria monitoring