Iowa DNR
ADBNet

Water Quality Assessments

Impaired Waters List

Beaver Creek IA 04-UDM-1233

mouth (S17 T79N R24W Polk Co.) to the Polk/Dallas county line (west line S18 T80N R25W Polk Co.

Assessment Cycle
2016
Release Status
Final
Data Collection Period
Overall IR Category
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Stable
Created
9/30/2016 10:40:09 AM
Updated
10/12/2016 1:51:03 PM
Assessment conducted in accordance with Iowa's 2016 IR methodology
Use Support
Class A1
Partially Supported
Bacteria: Indicator Bacteria- E. coli
Support Level
Partially Supported
Impairment Code
5p - Impairment occurs on a waterbody with a presumptive A1 or B(WW1) use.
Cause Magnitude
Moderate
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2008
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Ambient monitoring: Iowa DNR-rivers
TMDL Priority
Tier III
Class BWW2
Partially Supported
Biological: low aquatic macroinvertebrate IBI
Support Level
Partially Supported
Impairment Code
5b-v - Biological - verified
Cause Magnitude
Slight
Status
New
Source
Unknown: Source Unknown
Source Confidence
Low
Cycle Added
2016
Impairment Rationale
Low Biotic Index
Data Source
Biological monitoring: Iowa DNR WQMA
TMDL Priority
Tier IV
General Use
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 "partially supported" (IR 5p) due to levels of indicator bacteria that violate state water quality criteria. The Class B(WW2) aquatic life uses are assessed (evaluated) as "partially supported" (IR 5b-v) based on results of IDNR/SHL biological sampling in 2012 and 2013. The sources of data for this assessment are the results from the IDNR/SHL ambient monthly monitoring station on Beaver Creek east of Grimes (STORET station 10770001 (formerly station 420307) from 2012 through 2014 and IDNR/SHL biological (benthic macroinvertebrate) sampling conducted near Grimes in 2013 and 2013.

Assessment Explanation

The presumptive Class A1 (primary contact recreation) uses are assessed (monitored) as "partially supported" based on levels of indicator bacteria that exceeded state water quality criteria.  The geometric means of indicator bacteria (E. coli) in the 25 samples collected during the recreational seasons of 2012 through 2014 at IDNR station 10770001 were as follows: the 2012 geometric mean was 264 orgs/100 ml, the 2013 geometric mean was 380 orgs/100 ml, and the 2014 geometric mean was 282 orgs/100 ml.  All three recreation season geometric means exceeded the Class A1 geometric mean criterion of 126 orgs/100 ml.  Fifteen of the combined 25 samples (60%) exceeded Iowa’s 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 the geometric mean is greater than 126 orgs/100 ml., the primary contact recreation uses should be assessed as "impaired" (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 "partially supported."

Results of chemical/physical water quality monitoring at IDNR station 10770001 suggest “full support” of the aquatic life uses. Monitoring showed no violations of Class B(WW2) water quality criteria for 36 Ammonia samples (maximum = 0.8 mg/L), 36 Dissolved Oxygen samples (minimum = 6.4 mg/L), 36 pH samples (range = 7.3 to 8.7), 36 Chloride samples (maximum = 180 mg/L), or 36 Sulfate samples (maximum = 140 mg/L) occurred during monitoring from January 2012 to December 2014. One of the 36 samples (3%) analyzed for Temperature (maximum = 32.8° c) violated the Class B(WW2) criteria during the 2012-2014 monitoring period. According to U.S. EPA guidelines (U.S. EPA 1997b, page 3-17), a violation frequency of greater than 10% for conventional parameters such as Temperature suggests impairment of aquatic life uses. Because the frequency of violations for this parameter is not greater than 10 percent, these results do not suggest impairment of the Class B(WW2) aquatic life uses.

In contrast to the water quality aquatic life assessment, the aquatic life assessment based on biological sampling suggests the aquatic life uses are "partially supporting". This monitored biological assessment was based on data collected in 2012 and 2013 as part of the IDNR/SHL large river/stream nutrient 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 benthic macroinvertebrate taxa collected in the stream sampling reach. The biological metrics were combined a benthic macroinvertebrate index (BMIBI). The index rank the biological integrity of a stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum). The 2012 BMIBI score was 21 (poor) and the 2013 BMIBI score was 56 (good). The aquatic life use support was assessed (monitored) as "partially supporting" (=PS), based on a comparison of the BMIBI scores with biological impairment criteria (BIC) established from a statistical analysis of biological data collected at stream ecoregion reference sites from 1994-2008. The BMIBI BIC for this ecoregion is 62.  This segment passed the BMIBI BIC 0/2 times in the last five years.

This aquatic life assessment is now considered "monitored" 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 during a recent five year period to be considered “monitored”. This segment had two BMIBI samples collected in the last five years.

Monitoring and Methods
Assessment Key Dates
8/19/2013 Biological Monitoring
8/22/2012 Biological Monitoring
1/5/2012 Fixed Monitoring Start Date
12/3/2014 Fixed Monitoring End Date
Methods
230 Fixed station physical/chemical (conventional plus toxic pollutants)
315 Regional reference site approach
320 Benthic macroinvertebrate surveys
420 Indicator bacteria monitoring