Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Middle Fork Little Maquoketa River IA 01-TRK-138

Alternate name(s) for this segment: Bankston Creek

from west line of S31 T90N R1E (Dubuque Co.) to north line of S33 T90N R1W Dubuque Co.

Cycle
2018
Release Status
Final
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Unknown
Created
5/8/2019 8:00:46 AM
Updated
9/4/2019 9:20:54 AM
Use Support
Class A1
Recreation - Primary contact
Not Assessed
Class A2
Recreation - Secondary contact
Not Assessed
Class BCW1
Aquatic Life - Cold Water Type 1
Partially Supported
Support Level
Partially Supported
Impairment Code
5b-v - Biological - verified
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
Impairment Code
3b - Use potentially impaired based on an evaluated assessment.
Cause Magnitude
Moderate
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
Low
Cycle Added
2016
Impairment Rationale
Significantly > 10% of days fail to meet 16-hour criteria
Data Source
Special project/study: Iowa DNR
Impairment Code
3b - Use potentially impaired based on an evaluated assessment.
Cause Magnitude
Moderate
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
Low
Cycle Added
2016
Impairment Rationale
Significantly > 10% of samples fail to meet criterion
Data Source
Special project/study: Iowa DNR
Class HH
Human Health -
Not Assessed
General Use
General Use water -
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class B(CW1) coldwater aquatic life uses are assessed (monitored) as "partially supported" based on based on results of DNR/SHL cold water stream biological sampling in 2012 and 2016 and continuous DO/temperature monitoring in 2012.  An updated summary of trout reproduction in Iowa streams prepared by the DNR Fisheries Bureau in January 2019 suggests natural reproduction of trout occurs in the upper portion of this segment. The Class A1 (primary contact recreation) uses, Class A2 (secondary contact recreation) uses and Class HH (fish consumption) uses remain "not assessed" due to the lack of information upon which to base an assessment.

Assessment Explanation

The assessment of the Class B(CW1) aquatic life uses was based on data collected in 2012 and 2016 as part of the DNR/SHL cold water stream sampling project. A series of biological metrics which reflect coldwater 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 that were collected in the stream sampling reach. The biological metrics were combined to make a coldwater benthic index (CBI). The index ranks the biological integrity of a coldwater stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum). The 2012 CBI scores were 35 and 42.The 2016 CBI scores were 45 and 49.The aquatic life use support was assessed (evaluated) as partially supporting (=PS), based on a comparison of the CBI scores with biological impairment criteria (BIC) established for the 2012 Section 305(b) report.The biological impairment criteria were determined from a statistical analysis of data collected at coldwater stream reference sites from 1994-2011.The CW BIC is 60 and this segment passed the CW BIC 0/4 times in the last five years (2012-2016).

This aquatic life assessment is now considered "monitored" based on a change in the 2010 DNR assessment methodology. DNR now requires a segment have two or more biological samples collected from the segment in multiple years in a recent five-year period to be considered “monitored”. This segment had a multiple samples collected in the last five years (2012-2016).

Results of continuous dissolved oxygen (DO) and temperature monitoring in 2012 for the DNR/SHL coldwater stream sampling project suggest impairment of Class B(CW1) aquatic life uses. The lowest DO concentration recorded in 55 days of continuous monitoring was 5.7 mg/L. The daily DO minimum concentration failed to meet the 24-hour DO criterion (5 mg/L) in 0 of 55 days. The percentage exceeding (0%) was less than (passing) the 10% impairment threshold used to assess conventional water quality parameters. The associated statistical analysis confidence level was high (>90%). In contrast, the 16-hour DO criterion (7 mg/L) was exceeded in 10 of 55 days. The percentage exceeding (18%) was greater than (failing) the 10% threshold with high statistical confidence (>90%). The maximum stream temperature recorded during the sensor deployment period was 22.8 degrees (C). The B(CW1) temperature criterion of 20 (C) was exceeded in 22 of 55 days. The percentage exceeding (40%) was greater than (failing) the 10% impairment threshold with high statistical confidence (>90%). Based on these data, the B(CW1) aquatic life use is assessed as impaired due to DO and temperature. The assessment type is “evaluated” because it is based on data collected from a single year within the current data assessment period. In order to meet the requirements for a “monitored” assessment, the DNR’s continuous monitoring assessment methodology requires monitoring data from two or more years within the assessment period.

In contrast to the water quality and benthic macroinvertebrate data, an updated summary of trout reproduction in Iowa streams prepared by the DNR Fisheries Bureau in January 2019 suggests that the Class B(CW1) uses should be assessed as "fully supported". According to the updated summary, Middle Fork Little Maquoketa River (a.k.a. Bankston Cr.) is in the group of Iowa coldwater streams that support natural reproduction of trout. Based on results of surveys by the DNR Fisheries Bureau, the upper portion of this stream (~ 1 mile) is placed in the category of Iowa trout streams that exhibit consistent natural reproduction and maintain a wild population of Brown Trout without any stocking (Category I stream).

Monitoring and Methods
Assessment Key Dates
7/23/2012
Biological Monitoring
7/10/2012
Non-fixed Monitoring Start Date
9/15/2012
Non-fixed Monitoring End Date
7/18/2016
Biological Monitoring
8/31/2016
Biological Monitoring
9/4/2012
Biological Monitoring
1/1/2019
Biological Monitoring
Methods
120
Surveys of fish and game biologists/other professionals
222
Non-fixed-station monitoring (conventional during key seasons and flows)
315
Regional reference site approach
320
Benthic macroinvertebrate surveys
330
Fish surveys
380
Quantitative physical habitat assessment