Iowa DNR
Iowa DNR
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Water Quality Assessments
Impaired Waters List

Springbrook Creek IA 04-RAC-1202

mouth (S4 T80N R31W Guthrie Co.) to headwaters (Guthrie Co.)

Assessment Cycle
2010
Result Period
2006 - 2008
Designations
General Use
Assessment Methodology
Assessment Type
Evaluated
Integrated Report
Category 3b-u
Legacy ADBCode
IA 04-RAC-02415_0
Overall Use Support
Partial
Aquatic Life Use Support
Partial
Primary Contact Recreation
Not assessed
Documentation
Assessment Comments

Assessment remains based on 2001 IDNR/UHL biological monitoring data: FIBI = 32 (fair), BMIBI = 19 (poor). Non-riffle FIBI BIC = 32, BMIBI BIC = 62.

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 uses remain assessed (evaluated) as "partially supported"  based on results of IDNR/UHL biological monitoring in 2001.

EXPLANATION:  The assessment of aquatic life uses remains based on data collected in 2001 as part of the DNR/UHL stream biocriteria project.   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 that were 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 2001 FIBI score was 32 (fair) and the BMIBI score was 19 (poor).   The aquatic life use support was assessed 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 non-riffle FIBI BIC for this ecoregion is 32 and the BMIBI BIC for this ecoregion is 62.   Even though this site passed the FIB BIC and failed the BMIBI BIC, it is uncertain as to whether or not this segment is meeting the aquatic life criteria because it is a small headewater stream and doesn’t fall in the calibrated watershed size.

This assessment is considered “evaluated” (of lower confidence) due to the lack of a biological assessment protocol for general use-only streams.   IDNR’s existing protocol has been calibrated to aquatic life reference conditions in wadeable Class B(WW2) and Class B(WW1) streams.   The aquatic environment of most general use streams is one of extremes in water quality.   Consequently, general use-only streams tend to have biological diversity that is low relative to more stable aquatic environments of Class B(WW2) and Class B(WW1) streams.   Thus, the use of biological assessment methods developed for the ecologically more stable and diverse Class B(WW2) streams to assess general use reaches will likely overstate the existence of impairment.   For these reasons, general use-only stream reaches that show impairment based on a comparison of monitoring data to Class B(WW2) water quality criteria, or that show failure to meet regional expectations for aquatic biota (fish or aquatic macroinvertebrates) of Class B(WW2) streams, will not be added to Iowa’s Section 303(d) list of impaired waters (Category 5 of the Integrated Report).   The assessment type for these waters will be considered "evaluated" (indicating an assessment with relatively lower confidence) as opposed to “monitored" (indicating an assessment with relatively high confidence).   Such waters will be placed in either Category 2b or 3b of the IR and thus will be added to the state’s list of “waters in need of further investigation”.

Monitoring and Methods
Assessment Key Dates
7/11/2001 Biological Monitoring
7/11/2001 One-time Chemical 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
Monitoring Levels
Biological 4
Habitat 4
Physical Chemistry 1
Toxic 0
Pathogen Indicators 0
Other Health Indicators 0
Other Aquatic Life Indicators 0
# of Bio Sites 1
BioIntegrity Poor
Causes and Sources of Impairment
Causes Use Support Cause Magnitude Sources Source Magnitude
Cause Unknown Overall Use Support High
  • Source Unknown
  • High
Cause Unknown Aquatic Life Support High
  • Source Unknown
  • High
Noxious aquatic plants Overall Use Support High
  • Source Unknown
  • High
Noxious aquatic plants Aquatic Life Support High
  • Source Unknown
  • High