Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Ocheyedan River IA 06-LSR-1638

mouth (S13 T96N R37W Clay Co.) to confluence with Little Ocheyedan R. in S28 T98N R39W Osceola Co.

Cycle
2018
Release Status
Final
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Stable
Created
5/17/2019 9:59:49 AM
Updated
7/10/2019 3:05:47 PM
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
Low
Cycle Added
2008
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Ambient monitoring: Iowa DNR-rivers
TMDL Priority
Tier III
Class BWW2
Aquatic Life - Warm Water Type 2
WINOFI
Impairment Code
3b-c - Use potentially biologically impaired based on calibrated IBI metrics.
Cause Magnitude
Slight
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
Low
Cycle Added
2006
Impairment Rationale
Low Biotic Index
Data Source
Biological monitoring: Iowa DNR WQMA
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" due to levels of indicator bacteria that violate state water quality criteria. The Class B(WW2) aquatic life uses are assessed (evaluated) as "partially supported" based on results of DNR/SHL conducted in 2003, 2012 and 2013. However, the results from DNR/SHL monthly ambient chemical/physical water quality monitoring conducted upstream from Spencer at the County Road M-38 bridge southwest of Spencer from January 2012 through September 2014 (STORET station 10210001) suggest that the aquatic life uses of this segment should be assessed as "fully supporting".

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 22 samples collected during the recreational seasons of 2012 through 2014 at Ocheyedan River upstream of Spencer were as follows: the 2012 geometric mean was 149 orgs/100 ml, the 2013 geometric mean was 264 orgs/100 ml, and the 2014 geometric mean was 209 orgs/100 ml. All three recreation season geometric means exceeded the Class A1 geometric mean criterion of 126 orgs/100 ml. Ten of the combined 22 samples (45%) 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 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".

The assessment of the Class B(WW2) aquatic life uses was based primarily on biological data collected in 2003, 2012 and 2013 as part of the DNR/SHL REMAP and large river sampling projects. A series of biological metrics which 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 2003 FIBI score was 28 (fair) and the BMIBI score was 49 (fair). The 2012 BMIBI score was 61 (good) and the 2013 BMIBI score was 45 (fair). The aquatic life use support was assessed (evaluated) as partially supporting (=PS), based on a comparison of the FIBI and BMIBI scores with biological impairment criteria (BIC) established for previous Section 305(b) reports.The biological impairment criteria were determined from a statistical analysis of data collected at stream ecoregion reference sites from 1994-2008. The FIBI BIC for this ecoregion is 43 and the BMIBI BIC for this ecoregion is 54. This segment failed the FIBI BIC in 2003 and passed the BMIBI BIC 1/3 times in the last 14 years.

This aquatic life assessment is considered "evaluated" because there were not two or more samples collected from this segment in multiple years in a recent five year period. 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).

Conversely, the chemical/physical monitoring at the DNR/SHL city station southwest of Spencer showed no violations of Class B(WW2) water quality criteria for 32 Ammonia samples (maximum = 1.7 mg/L), 33 Dissolved Oxygen samples (minimum = 5.4 mg/L), 32 pH samples (range = 7.5 to 8.6), 33 Temperature samples (maximum = 27.9° c), 33 Chloride samples (maximum = 38 mg/L), or 33 Sulfate samples (maximum = 300 mg/L) occurred during monitoring from January 2012 to September 2014. 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(WW2) aquatic life uses.

Monitoring and Methods
Assessment Key Dates
1/9/2012
Fixed Monitoring Start Date
9/8/2014
Fixed Monitoring End Date
7/24/2003
Biological Monitoring
8/14/2012
Biological Monitoring
10/8/2013
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
380
Quantitative physical habitat assessment
420
Indicator bacteria monitoring