Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Little Bear Creek IA 02-IOW-705

mouth (S16 T80N R13W Poweshiek Co.) to confluence with unnamed tributary in SE 1/4 NW 1/4 S29 T80N R14W Poweshiek Co.

Cycle
2018
Release Status
Final
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Unknown
Created
5/14/2019 7:19:17 AM
Updated
7/18/2019 3:00:59 PM
Use Support
Class A1
Recreation - Primary contact
Not Supported
Support Level
Not Supported
Impairment Code
5p - Impairment occurs on a waterbody with a presumptive A1 or B(WW1) use.
Cause Magnitude
High
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2014
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Special project/study
TMDL Priority
Tier III
Class BWW2
Aquatic Life - Warm Water Type 2
Partially Supported
Support Level
Partially Supported
Impairment Code
5b-t - Biological - tentative
Cause Magnitude
Slight
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
Low
Cycle Added
2008
Impairment Rationale
Low Biotic Index
Data Source
Biological monitoring: Iowa DNR WQMA
TMDL Priority
Tier IV
General Use
General Use water -
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The presumptive Class A1 (primary contact recreation) uses are assessed (monitored) as “not supporting” due to levels of indicator bacteria that exceed state water quality standards.  The Class B(WW2) aquatic life uses remain assessed (evaluated) as “partially supporting based on DNR/SHL biological sampling data from 2005 and 2010.  The sources of data for this assessment include the results of monitoring as part of the Little Bear Creek Watershed Monitoring Project from September 2012 to October 2014 at two stations:  (moving from downstream to upstream):  (1) Site LB-6 at 385th Avenue (STORET ID 15790006) and (2) Site LB-4 at S. Orchard Street (in Brooklyn) (STORET ID 15790004).

Assessment Explanation

The presumptive Class A1 uses are assessed (monitored) as "not supported" based on results of bacteria monitoring from September 2012 through October 2014. Five samples were collected during the recreation seasons of 2012, and 10 samples were collected at each station during both recreation seasons of 2013 and 2014 (total of 25 samples at each station during the 2012-2014 monitoring period). The recreation season geometric means at Station LB-6 from 2012 through 2014 were 1,266 orgs/100 ml, 1,283 orgs/100 ml, and 1,429 orgs/100 ml, respectively. The recreation season geometric means at Station LB-4 from 2012 through 2014 were 1,082 orgs/100 ml, 749 orgs/100 ml, and 1,105 orgs/100 ml, respectively. Twenty-four of the 25 samples collected at each monitoring site (96%) exceeded the single-sample maximum criterion of 235 orgs/100 ml. According to U.S. EPA guidelines for Section 305(b) reporting and according to DNR’s assessment/listing methodology, if the geometric mean level of E. coli is greater than the state criterion, the primary contact recreation uses should be assessed as "impaired" (see pgs 3-33 to 3-3of U.S. EPA 1997b).

The Class B(WW2) aquatic life uses are assessed (evaluated) as “partially supporting” based on data collected in 2005 and 2010 as part of the DNR/SHL stream REMAP project. A series of biological metrics which 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 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 2005 FIBI score was 34 (fair) and the BMIBI score was 39 (fair). The 2010 FIBI score was 35 (fair) and the BMIBI score was 52 (fair). 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 for previous Section 305(b) reports. This site passed the FIBI BIC 0/2 times and the BMIBI BIC 1/2 times in the last 12years. The FIBI BIC for this ecoregion is 36 and the BMIBI BIC for this ecoregion is 51. The biological impairment criteria were determined from a statistical analysis of data collected at stream ecoregion reference sites from 1994-2008.

This aquatic life assessment is considered "evaluated" because there were not two or more samples collected from this segment in multiple years over a recent five-year period. According to DNR’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). DNR 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-t and remains on Iowa’s Section 303(d) list of impaired waters.

Results of chemical/physical monitoring at sites LB4 and LB6 from 2012 through 2014, however, do not suggest impairment of the Class B(WW2) uses. No violations of Class B(WW2) criteria occurred for the following parameters monitored at Site LB4 and LB6 during the 2012-2014 period: ammonia (20 combined samples), pH (40 combined samples), temperature (40 combined samples) and chloride (30 combined samples). Two of 20 samples (10%) violated the Class B(WW2) criterion for dissolved oxygen at Site LB4, and one of 20 samples violated this criterion at Site LB6. These monitoring results, however, do not suggest impairment of the Class B(WW2) aquatic life uses. According to U.S. EPA guidelines for Section 305(b) reporting, if more than 10% of samples exceed state criteria for conventional parameters such as dissolved oxygen, the aquatic life uses should be assessed as "impaired" (see pgs 3-33 to 3-35 of U.S. EPA 1997b). According to DNR’s assessment/listing methodology, however, the dissolved oxygen violation frequencies at sites LB4 and LB6 do not indicate that significantly greater than 10% of the samples exceed the Class B(WW2) criterion. Thus, the results of chemical/physical water quality monitoring from 2012 to 2014 in this segment do not indicate impairment of the Class B(WW2) aquatic life uses.

Monitoring and Methods
Assessment Key Dates
8/18/2005
Biological Monitoring
8/24/2010
Biological Monitoring
9/17/2012
Fixed Monitoring Start Date
10/15/2014
Fixed Monitoring End Date
Methods
150
Monitoring data more than 5 years old
240
Non-fixed station physical/chemical (conventional + toxicants)
315
Regional reference site approach
320
Benthic macroinvertebrate surveys
330
Fish surveys
380
Quantitative physical habitat assessment
420
Indicator bacteria monitoring