Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Bear Creek IA 06-LSR-1833

from mouth (SE1/4 SW1/4 S13 T93N R41W Cherokee Co.) to headwaters in NW1/4 S5 T92N R41W Cherokee Co.

Cycle
2018
Release Status
Final
Overall IR
3 - Insufficient data exist to determine whether any designated uses are met.
Trend
Unknown
Created
5/2/2019 1:32:44 PM
Updated
7/30/2019 7:43:16 AM
Use Support
Class A1
Recreation - Primary contact
Not Assessed
Class BWW1
Aquatic Life - Warm Water Type 1
WINOFI
Impairment Code
3b - Use potentially impaired based on an evaluated assessment.
Cause Magnitude
Moderate
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2016
Impairment Rationale
Potential Impairment
Data Source
Fish kill investigation: Iowa DNR
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 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 a fish kill that occurred in this assessment segment in September 2015.  No cause of the fish kill was determined; thus, this potential impairment will be placed in IR Category 3b. Results of DNR/SHL biological (REMAP) sampling in 2002 suggest the presumptive Class B(WW1) aquatic life be assessed (evaluated) as "fully supported".

Assessment Explanation

The presumptive Class B(WW1) aquatic life uses remain assessed as “partially supported” (IR 3b) due to a fish kill that occurred on or before September 28, 2015, 4 miles NW of Meriden at K and L avenue bridges. The following are notes from the fish kill investigation:

FO3 received a page early on Saturday morning from a chub fisherman near Meriden in Cherokee County. He said there were “hundreds” of dead chubs and minnows under a bridge north of Meriden in Bear Creek. Bear Creek flows northeasterly from that point about one mile and discharges into Mill Creek. Water quality parameters were normal with high DO and low ammonia. Dead fish were only observed under two bridges. The second bridge, on C16 right before Bear Creek enters Mill Creek, had a few floaters that appeared to come from a pooled area under the bridge at L Avenue where most of the dead fish were observed, just south of County Road C16. Flows in the creeks were high from rains in the area over the past few weeks. No dying fish were observed. This area had received approximately 1 inch of rain during the previous two days. We contacted two cattle facilities in the area but saw no evidence of runoff. It is possible some pollutants entered the stream and were washed away by the time we responded. Fisheries personnel did not conduct a count as no obvious source was determined. It is also possible that DO levels dropped in the pooled water overnight, killing fish, and then returned to normal. It is also possible that the fish died of “natural” causes.

No estimates were provided for the number of fish killed, the value of the fish killed, or the cost of the Iowa DNR investigation. The kill affected approximately 1 mile of stream.

According to DNR’s assessment/listing methodology, the occurrence of a single pollutant-caused fish kill, or a fish kill of unknown origin, on a waterbody or waterbody reach during the most recent assessment period (2012-2016) indicates a severe stress to the aquatic community and suggests that the aquatic life uses should be assessed as “impaired”. If a cause of the kill was not identified during the DNR investigation, or if the kill was attributed to non-pollutant causes (e.g., winterkill), the assessment type will be considered “evaluated.” Such assessments, although suitable for Section 305(b) reporting, lack the degree of confidence to support addition to the state Section 303(d) list of impaired waters (IR Category 5). Waterbodies affected by such fish kills will be placed in IR subcategories 2b or 3b and will be added to the state list of waters in need of further investigation.

The assessment of the presumptive Class B(WW1) aquatic life uses was also based on data collected in 2002 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 biocriteria sampling data. The biological metrics are based on the numbers and types of 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). The index ranks the biological integrity of a stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum). The 2002 FIBI score was 36 (fair). The aquatic life use support was assessed (evaluated) as fully supporting (=FS), 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 1994-2008. The FIBI BIC for this ecoregion is 43. Even though this site passed the FIBI BIC (using the FIBI uncertainty adjustment value of 7 points applied to single samples), 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. 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).

Monitoring and Methods
Assessment Key Dates
10/15/2002
Biological Monitoring
9/28/2015
Fish Kill
Methods
120
Surveys of fish and game biologists/other professionals
140
Incidence of spills and/or fish kills
150
Monitoring data more than 5 years old
315
Regional reference site approach
330
Fish surveys
380
Quantitative physical habitat assessment