Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Little Sioux River IA 06-LSR-1577

from confluence with Ocheyedan R. at Spencer (S13 T96N R37W Clay Co.) to confluence with Milford Cr. in NW 1/4 S14 T98N R37W Dickinson Co.

Cycle
2018
Release Status
Final
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Stable
Created
5/31/2019 7:24:40 AM
Updated
7/10/2019 2:13:33 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 BWW1
Aquatic Life - Warm Water Type 1
WINOFI
Impairment Code
3b-u - Use potentially biologically impaired based on uncalibrated 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
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 "not supported" due to levels of indicator bacteria that violate state water quality criteria. The Class B(WW1) aquatic life uses are assessed (evaluated) as "partially supported" based on results of DNR/SHL biological sampling conducted in 2012, 2013 and 2016. Fish consumption uses remain "not assessed" due to the lack of fish contaminant monitoring in this river segment The sources of data for this assessment is the results of monthly monitoring from 2012 through 2014 at the DNR/SHL ambient city monitoring station located upstream from Spencer at the Highway 18 bridge northwest of Spencer (STORET station 10210002) and 2012, 2013 and 2016 DNR/SHL biological sampling near Spencer.

Assessment Explanation

The Class A1 (primary contact recreation) are assessed 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 the Little Sioux River upstream of Spencer were as follows: the 2012 geometric mean was 112 orgs/100 ml, the 2013 geometric mean was 144 orgs/100 ml, and the 2014 geometric mean was 193 orgs/100 ml. Two of the three recreation season geometric means exceeded the Class A1 geometric mean criterion of 126 orgs/100 ml. Eleven of the combined 22 samples (50%) 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"

Based exclusively on the results of ambient water quality monitoring, Class B(WW1) aquatic life uses should be assessed (monitored) as "fully supported". Monitoring at the DNR/SHL city station upstream from Spencer showed no violations of Class B(WW1) water quality criteria for 32 Ammonia samples (maximum = 1.1 mg/L), 33 Dissolved Oxygen samples (minimum = 5.3 mg/L), 32 pH samples (range = 7.6 to 8.9), 33 Temperature samples (maximum = 29.7 °C), 33 Chloride samples (maximum = 41 mg/L), or 33 Sulfate samples (maximum = 150 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(WW1) aquatic life uses.

This (evaluated) assessment of the Class B(WW1) aquatic life uses was based on data collected in 2012, 2013 and 2016 as part of the DNR/SHL large river sampling project. 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 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 2012 and 2013 BMIBI scores were 18 (poor) and 31 (fair). The 2016 FIBI score was 51 (good) and the BMIBI scores were 70, 70 (both good). 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 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 assessment is considered evaluated because the drainage area (536 mi2) above this sampling site was greater than the maximum limit (500 mi2) that was used to calibrate the Iowa wadeable stream impairment criteria. Even though this site passed the FIBI BIC (1/1) but failed the BMIBI BIC (2/4), it is uncertain as to whether or not this segment is meeting the aquatic life criteria because the site used for the assessment doesn’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 contaminant monitoring data for this river segment.

Monitoring and Methods
Assessment Key Dates
1/1/2012
Fixed Monitoring Start Date
9/8/2014
Fixed Monitoring End Date
8/14/2012
Biological Monitoring
9/10/2013
Biological Monitoring
8/2/2016
Biological Monitoring
9/13/2016
Biological Monitoring
Methods
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