Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

South Minerva Creek IA 02-IOW-6284

from mouth (T85N R20W Sec35 Marshall Co.) to headwaters (T84N R21W Sec9 Story Co.)

Assessment Cycle
2012
Result Period
2008 - 2010
Designations
Class A1 Class B(WW-1)
Assessment Methodology
Assessment Type
Evaluated
Integrated Report
Category 3b-u
Legacy ADBCode
IA 02-IOW-0255_0
Overall Use Support
Partial
Aquatic Life Use Support
Partial
Primary Contact Recreation
Not assessed
Documentation
Assessment Comments

Assessment based on 2007 and 2008 IDNR/UHL biological monitoring data: FIBI = 33, 34, 40 (all fair) and 54 (good); BMIBI = 24 (poor), 36, 50 (both fair) and 60 (good). Non-riffle habitat FIBI BIC = 32, riffle habitat BIC = 53 and 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.]

SUMMARY:  The presumptive Class A1 (primary contact recreation) uses are "not assessed" due to the lack of information upon which to base an assessment.    The presumptive Class B(WW1) aquatic life uses are assessed (evaluated) as "partially supported" based on results of IDNR/UHL biological monitoring in 2007 and 2008.  

EXPLANATION:  The assessment of the presumptive Class B(WW1) aquatic life uses is based on data collected in 2007 and 2008 as part of the IDNR/UHL headwater stream sampling 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 2007 FIBI scores were 33, 34 and 40 (all fair); the 2008 FIBI score was 54 (good).   The 2007 BMIBI scores were 24 (poor), 50 (fair) and 60 (good); the 2008 BMIBI score was 36 (fair).   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 non-riffle habitat FIBI BIC for this ecoregion is 32, the riffle habitat FIBI BIC is 53 and the BMIBI BIC is 62.   This segment passed the FIBI BIC 3/4 times and passed the BMIBI BIC 0/4 times in the last five years.   Even though this site passed the FIBI BIC (3/4) and failed to meet the BMIBI 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.  

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).  

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
8/21/2008 Biological Monitoring
9/27/2007 Biological Monitoring
8/22/2007 Biological Monitoring
8/8/2007 Biological Monitoring
Methods
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 1
Toxic 0
Pathogen Indicators 0
Other Health Indicators 0
Other Aquatic Life Indicators 0
# of Bio Sites 2
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