Iowa DNR
ADBNet

Water Quality Assessments

Impaired Waters List

East Nodaway River IA 05-NOD-1391

mouth (S6 T67N R36W Page Co.) to confluence with Long Branch Cr at S17-18 line T70N R35W Taylor Co.

Assessment Cycle
2014
Result Period
2010 - 2012
Designations
Class A1 Class B(WW-1) Class HH
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 5p
Legacy ADBCode
IA 05-NOD-0030_1
Overall Use Support
Not supporting
Aquatic Life Use Support
Partial
Fish Consumption
Not assessed
Primary Contact Recreation
Not supporting
Documentation
Assessment Comments

Assessment based on: (1) results of IDNR/SHL monthly ambient water quality monitoring conducted during the 2010-2012 assessment period at the State Highway 2 bridge 2 miles east of Clarinda (STORET station 10730002 (formerly station 780809)) and (2) results of IDNR/SHL biocriteria monitoring in 2004 & 2012.

Basis for Assessment

[Note:  Prior to the 2008 Section 305(b) cycle, this stream segment was designated only for Class B(WW) 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), this segment is also now presumptively 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 presumptive Class A1 (primary contact recreation) uses are assessed (monitored) as "not 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 "partially supported" (IR 3b-c) based on results of biological sampling in 2004 and 2012.   Fish consumption uses remain assessed "not assessed" (IR 3a) due to the lack of fish contaminant monitoring in this river reach.   This assessment is based on (1) results of IDNR/SHL monthly ambient water quality monitoring conducted during the 2010-2012 assessment period at the State Highway 2 bridge 2 miles east of Clarinda (STORET station 10730002 (formerly station 780809)) and (2) results of IDNR/SHL biocriteria sampling in 2004 and 2012.  

EXPLANATION:  The presumptive Class A1 (primary contact recreation) are assessed as "not 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 2010 through 2012 at the East Nodaway River near Clarinda were as follows:  the 2010 geometric mean was 261 orgs/100 ml, the 2011 geometric mean was 272 orgs/100 ml and the 2012 geometric mean was 812 orgs/100 ml.   All three geometric means exceed the Class A1 criterion of 126 orgs/100 ml.   Twelve of the 24 samples (50%) 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 are "not supported" (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 “impaired.”  

Regarding support of the Class B(WW1) aquatic life uses, results of monitoring at the IDNR/UHL ambient monitoring station east of Clarinda showed no violations of Class B(WW1) water quality criteria during the 2010-2012 assessment period for dissolved oxygen (minimum value = 6.7 mg/l), pH (range = 7.2 to 8.8 units), ammonia-nitrogen (maximum value = 0.36 mg/l), chloride, sulfate, or water temperature in the approximately 36 samples analyzed.  These results suggest "full support" of the Class B(WW1) aquatic life uses.  

Results of biological sampling, however, suggest that the Class B(WW1) uses should be assessed (evaluated) as "partially supported" based on IDNR/SHL biocriteria sampling in 2004 and 2012.   The 2004 FIBI score was 23 (poor) and the BMIBI score was 46 (fair).   The 2012 FIBI score was 39 (fair) and the BMIBI score was 46 (fair).   This suggests the aquatic life use support be assessed as partially supported (=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 31 and the BMIBI BIC for this ecoregion is 54.   This segment passed the FIBI BIC 1/2 times and passed the BMIBI BIC 0/2 times in the last nine years.  

This aquatic life assessment is now considered "evaluated" based on a change in the 2010 IDNR assessment methodology.   IDNR now requires a segment have two or more biological samples collected from the segment in multiple years in a recent five year period to be considered “monitored”.   This segment had multiple samples collected in the previous nine years; however, the multiple samples were not collected during a recent five year period.    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 tissue monitoring in this river reach.

Monitoring and Methods
Assessment Key Dates
12/3/2012 Fixed Monitoring End Date
8/21/2012 Biological Monitoring
1/4/2010 Fixed Monitoring Start Date
10/13/2004 Biological Monitoring
Methods
220 Non-fixed station physical/chemical monitoring (conventional pollutant only)
315 Regional reference site approach
330 Fish surveys
380 Quan. measurements of instream parms-- channel morphology-- floodplain-- 1-2 seasons-- by prof
230 Fixed station physical/chemical (conventional plus toxic pollutants)
420 Water column surveys (e.g. fecal coliform)
320 Benthic macroinvertebrate surveys
Monitoring Levels
Biological 4
Habitat 4
Physical Chemistry 3
Toxic 3
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 Moderate
  • Source Unknown
  • High