Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Dry Creek IA 06-BSR-1878

mouth (T94N R48W Sec4 Sioux Co.) to headwaters (T97N R45W Sec32) Sioux Co.

Cycle
2018
Release Status
Final
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Unknown
Created
7/29/2019 12:36:38 PM
Updated
7/29/2019 12:40:16 PM
Use Support
Class A1
Recreation - Primary contact
Not Assessed
Class BWW1
Aquatic Life - Warm Water Type 1
Partially Supported
Support Level
Partially Supported
Impairment Code
5b-t - Biological - tentative
Cause Magnitude
Moderate
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
Low
Cycle Added
2006
Impairment Rationale
Low Biotic Index
Data Source
Biological monitoring: Iowa DNR WQMA
TMDL Priority
Tier IV
Support Level
Partially Supported
Impairment Code
5b - Biological impairment or pollutant-caused fish kill - unknown source. No administrative action.
Cause Magnitude
Moderate
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2006
Impairment Rationale
Non Pollutant-caused fish kill
Data Source
Fish kill investigation: Iowa DNR
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 remain "not assessed" due to the lack of information upon which to base an assessment. The presumptive Class B(WW1) aquatic life uses of this waterbody remain assessed as “partially supported” based on 2003 fish kill. Results of biological sampling also suggest impairment of the presumptive Class B(WW1) aquatic life use. The sources of data for this assessment include (1) results of DNR/SHL biological (REMAP) sampling in 2004, 2005 and 2006 and (2) results of an DNR investigation of a fish kill in September 2003. The apparent lack of fish in this stream segment, as documented by the DNR/SHL 2004-2006 biological sampling results, continues to suggest a severe water quality impact and overwhelming evidence of impairment that justifies keeping this segment on Iowa’s Section 303(d) list.

Assessment Explanation

Results of stream REMAP biological sampling in 2004-2006 suggest that the presumptive Class B(WW1) aquatic life uses of this stream segment should be assessed (evaluated) as "partially supported". This assessment was based on biological data collected in 2004-2006 as part of the DNR/SHL stream REMAP 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 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 2004 FIBI score was 0 (poor) and the BMIBI score was 28 (poor). The 2005 FIBI score was 0 (poor) and the BMIBI score was 40 (fair). The 2006 FIBI score was 0 and the BMIBI score was 42 (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 1994-2008. The FIBI BIC for this ecoregion is 43 and the BMIBI BIC for this ecoregion is 54. This segment passed the FIBI BIC 0/3 times and passed the BMIBI BIC 0/3 times in the last nine years. Even though this site failed both the FIBI and BMIBI BICs, 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. Also, 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).

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 was previously on Iowa’s Section 303(d) list and thus remains on Iowa’s Section 303(d) list of impaired waters.

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. DNR’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.

In addition to results of biological monitoring that suggest impairment, the occurrence of a fish kill in September 2003 also suggests impairment of the aquatic life uses of this stream. This kill occurred on or before September 13, 2003; the kill was attributed to low levels of dissolved oxygen in a oxbow/backwater of Dry Creek. An estimated 1,501 fish were killed. According to the fish kill report; all fish were common carp except one crappie. No estimated value of the fish killed was provided. No estimate was provided for the size of the waterbody affected by the kill. The kill occurred in a backwater of Dry Creek at the southwest edge of Hawarden, IA; the location point for the kill is the NW1/4 of the SW1/4 of Section 2, T94N, R48W, Sioux County. According to the DNR investigation, dead fish were concentrated in a small backwater oxbow. Heavy rains in the area on September 13 may have allowed the carp to move into backwaters and oxbow; when stream level dropped the fish were trapped in the oxbow with no oxygen or water. A reporter noticed a muddy smell on 9/14 and noticed that fish were dying. During the investigation, oxygen levels were greater than 15 ppm and ammonia levels ranged from 1.0 to 1.5 ppm. The water was clear to mud stained. The kill was attributed to natural causes. This kill and others that occurred in smaller streams in northwest Iowa from September 11-15, 2003 were believed related to a rainfall event or events that followed a prolonged dry period. None of the investigations of these kills, however, suggested a specific pollutant-related cause.

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 indicates a severe stress to the aquatic community and suggests that the aquatic life uses should be assessed as “impaired”. Because the 2003 fish kill on this stream resulted in addition of this segment to Category 5b of Iowa's 2006 Integrated Report, this segment remains in Category 5b of Iowa's Integrated Report.

Monitoring and Methods
Assessment Key Dates
7/12/2006
Biological Monitoring
7/5/2005
Biological Monitoring
6/28/2004
Biological Monitoring
9/13/2003
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
320
Benthic macroinvertebrate surveys
330
Fish surveys
380
Quantitative physical habitat assessment