Iowa DNR
ADBNet

Water Quality Assessments

Impaired Waters List

Little Sioux River IA 06-LSR-1565

from confluence with Maple R. (S17 T83N R44W Monona Co.) to confluence with Big Cr. in Anthon in S4 T87N R43W Woodbury Co.

Assessment Cycle
2010
Result Period
2006 - 2008
Designations
Class A1 Class B(WW-1) Class HH
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 5a
Legacy ADBCode
IA 06-LSR-0020_1
Overall Use Support
Not supporting
Aquatic Life Use Support
Partial
Fish Consumption
Not assessed
Primary Contact Recreation
Not supporting
Documentation
Assessment Comments

Assessment is based on results of IDNR/UHL monthly ambient monitoring conducted during the 2006-2008 assessment period NE of Smithland (STORET station 10970001 (formerly station 911078)) and 2006 IDNR/UHL stream REMAP biological sampling near Rodney.

Basis for Assessment

[Note:  Prior to the 2008 Section 305(b) cycle, this river segment was designated only for Class B(WW1) aquatic life uses, including fish consumption uses.   Due to changes in Iowa’s surface water classification that were approved by U.S.  EPA in February 2008 (see http://www.iowadnr.com/water/standards/files/06mar_swc.pdf) and the results of an Use Attainability Analysis, this segment is also now designated for Class A1 (primary contact recreation) uses.   This segment remains designated for warmwater aquatic life use (now termed Class B(WW1) uses), and for fish consumption uses (now termed Class HH (human health/fish consumption uses).]

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 (monitored) as "fully supported" based on results of ambient chemical/physical water quality monitoring from 2006 through 2008 and are assessed as "partially supported" (evaluated) based on 2006 IDNR/UHL stream REMAP biological sampling near Rodney.   Fish consumption uses remain "not assessed" due to the lack of recent fish contaminant monitoring in this river segment.   This assessment is based on results of IDNR/UHL monthly ambient monitoring conducted during the 2006-2008 assessment period NE of Smithland (STORET station 10970001 (formerly station 911078)) and 2006 IDNR/UHL stream REMAP biological sampling near Rodney.  

EXPLANATION:  The Class A1 uses are assessed (monitored) as "not supported" based on results of ambient monitoring for indicator bacteria (E.  coli).   The geometric mean level of indicator bacteria (E.  coli) in the 21 samples collected at the IDNR/UHL ambient monitoring station northeast of Smithland during summer recreational seasons of 2006-2008 (749 orgs/100ml) far exceeds the Iowa Class A1 water quality criterion of 126 orgs/100ml.   Thirteen of the 21 samples (62%) exceed Iowa’s single-sample maximum criterion of 235 orgs/100 ml.   According to U.S.  EPA guidelines for Section 305(b) reporting and according to IDNR’s assessment/listing methodology, if the geometric mean level of E.  coli is greater than the state criterion of 126 orgs/100 ml., the primary contact recreation uses should be assessed as "not supported" (see pgs 3-33 to 3-35of U.S.  EPA 1997b).  

Regarding support of the Class B(WW1) aquatic life uses, monitoring at the IDNR/UHL ambient station northeast of Smithland showed no violations of Class B(WW1) water quality criteria for pH (range = 7.7 to 8.5), dissolved oxygen (minimum value = 6.4 mg/l) or ammonia nitrogen (maximum value = 1.3 mg/l) in the approximately 33 samples analyzed during the 2006-2008 period.   In addition, levels of toxic metals in the two samples analyzed, were all below their respective Class B(WW1) criteria.   (Note: pesticides were not monitored during the 2006 to 2008 period.)  Similar to the previous assessment periods, these results suggest "full support" of the Class B(WW1) aquatic life uses.

However, the results of the 2006 IDNR/UHL stream REMAP biological sampling near Rodney suggest only "partial support" of the Class B(WW1) aquatic life uses.   This evaluated biological assessment was based on data collected in 2006 as part of the IDNR/UHL 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 score was 12 (poor) and the BMIBI score was 62 (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 1994-2004.   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 (2713 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 failed to meet the FIBI BIC and passed the BMIBI BIC, it is uncertain as to whether or not this segment is meeting the aquatic life criteria because it doesn’t fall in the calibrated watershed size.  

Fish consumption uses remain "not assessed" due to a lack of recent fish contaminant monitoring in this river segment.

Monitoring and Methods
Assessment Key Dates
12/9/2008 Fixed Monitoring End Date
7/18/2006 Biological Monitoring
1/4/2006 Fixed Monitoring Start Date
Methods
230 Fixed station physical/chemical (conventional plus toxic pollutants)
420 Water column surveys (e.g. fecal coliform)
220 Non-fixed station physical/chemical monitoring (conventional pollutant only)
315 Regional reference site approach
320 Benthic macroinvertebrate surveys
330 Fish surveys
380 Quan. measurements of instream parms-- channel morphology-- floodplain-- 1-2 seasons-- by prof
Monitoring Levels
Biological 4
Habitat 4
Physical Chemistry 3
Toxic 1
Pathogen Indicators 3
Other Health Indicators 0
Other Aquatic Life Indicators 0
# of Bio Sites 1
BioIntegrity Fair
Causes and Sources of Impairment
Causes Use Support Cause Magnitude Sources Source Magnitude
Cause Unknown Aquatic Life Support Not Impairing
  • Source Unknown
  • Not Impairing
Pathogens Primary Contact Recreation High
  • Source Unknown
  • High