Iowa DNR
Iowa DNR
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Water Quality Assessments
Impaired Waters List

Saunders Branch IA 03-SKU-902

mouth (SW 1/4 S17 T71N R6W Henry Co.) to headwaters

Assessment Cycle
2010
Result Period
2006 - 2008
Designations
General Use Class A1 Class B(WW-1)
Assessment Methodology
Assessment Type
Evaluated
Integrated Report
Category 5b-t
Legacy ADBCode
IA 03-SKU-0085_0
Overall Use Support
Partial
Aquatic Life Use Support
Partial
Primary Contact Recreation
Not assessed
Documentation
Assessment Comments

Assessment remains based on 1998 IDNR/UHL biological monitoring data: FIBI scores = 20, 24 (both poor) and 32, 37 (both fair). FIBI BIC = 33.

Basis for Assessment

[Note:  Prior to the 2008 Section 305(b) cycle, this stream segment was classified only for general 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 now presumptively designated for Class A1 (primary contact recreation) uses and for Class B(WW1) aquatic life uses.   According to the Iowa Water Quality Standards, all perennial rivers and streams and all intermittent streams with perennial pools that are not specifically listed in the Iowa surface water classification are designated as Class A1 and Class B(WW1) waters.   Thus, for the current (2010) assessment, perennial flow is presumed, and the available water quality monitoring data will be compared to the applicable Class A1 and Class B(WW1) water quality criteria.]

SUMMARY:  The presumptive Class A1 (primary contact recreation) uses remain "not assessed" due to the lack of information upon which to base an assessment.   The presumptive Class B(WW1) aquatic life are assessed (evaluated) as "partially supported"  based on results of IDNR/UHL biological (biocriteria) sampling in 1998.   The biological monitoring data are now greater than five years old; therefore, this assessment is now considered "evaluated" instead of "monitored".   All of the FIBI scores increased compared to what was reported in previous Section 305(b) reports but the segments is still not meeting Biological Impairment Criteria.   Prior to the 2008 Section 305(b) assessment cycle, the FIBI scores were calculated using erroneous data.  

Note:  the data from the 1998 biological sampling are approximately 10 years old and are thus of questionable utility for assessing current water quality and biological conditions.   Because, however, this segment is a 303(d) listed water, the impairment will remain until monitoring is conducted to show “full support” of the aquatic life uses.  

EXPLANATION:  The evaluated biological assessment of the aquatic life uses (“partially supported”) was based on data collected in 1998 as part of the IDNR/UHL stream biological 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 fish species collected in the stream sampling reach.   The biological metrics were combined to make a fish community index of biotic integrity (FIBI).   The indexes rank the biological integrity of a stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum).   The 1998 FIBI scores were 20, 24 (both poor) and 32, 37 (both fair).   The aquatic life use support was assessed (evaluated) as partially supporting (=PS), based on a comparison of the FIBI score 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 33.   This segment passed the FIBI BIC 0/4 times in the last 11 years.    Even though this site failed to meet the FIBI BIC, it is uncertain as to whether or not this segment is meeting the aquatic life criteria because it is a small headwater stream and doesn’t fall in the calibrated watershed size.

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 between 2004 and 2008 to be considered “monitored”.     This segment had multiple samples collected in the previous 11 years (1998-2008); however, the samples were not collected during 2004-2008 and were not collected in multiple years.   Additionally, because these data are now considered too old (greater than five years) to accurately characterize current water quality conditions, the assessment category is considered “evaluated” (indicating an assessment with relatively lower confidence) as opposed to "monitored" (indicating an assessment with relatively higher confidence).   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).   However, despite this change in assessment methodology and type, this waterbody remains in IR Category 5b and remains on Iowa’s 2010 Section 303(d) list of impaired waters.

Prior to the changes in Iowa’s surface water classification that were approved by U.S.   EPA in February 2008, this stream was classified only for general uses due to the inability of the stream to support a viable aquatic community at low-flow conditions.   IDNR’s existing biological assessment protocol, however, was calibrated to aquatic life reference conditions in larger wadeable streams with perennial flow.   The aquatic environment of most headwater streams is one of extremes in water quality.   Consequently, intermittent headwater streams tend to have biological diversity that is low relative to more stable aquatic environments of larger streams with perennial flow.   Thus, the use of biological assessment methods developed for the ecologically more stable and diverse streams will likely overstate the existence of impairment in headwater streams.

Monitoring and Methods
Assessment Key Dates
10/13/1998 Biological Monitoring
Methods
320 Benthic macroinvertebrate surveys
330 Fish surveys
380 Quan. measurements of instream parms-- channel morphology-- floodplain-- 1-2 seasons-- by prof
220 Non-fixed station physical/chemical monitoring (conventional pollutant only)
315 Regional reference site approach
150 Monitoring data more than 5 years old
Monitoring Levels
Biological 3
Habitat 4
Physical Chemistry 1
Toxic 0
Pathogen Indicators 0
Other Health Indicators 0
Other Aquatic Life Indicators 0
# of Bio Sites 4
BioIntegrity Poor
Causes and Sources of Impairment
Causes Use Support Cause Magnitude Sources Source Magnitude
Priority organics Aquatic Life Support High
  • Hazardous Waste
  • Land Disposal
  • High
  • High
Unionized Ammonia Aquatic Life Support High
  • Municipal Point Sources
  • High
Organic enrichment/Low DO Aquatic Life Support High
  • Municipal Point Sources
  • High