Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

English Creek IA 04-LDM-1057

mo to Long Branch S16T74NR20W MarionCo

Cycle
2022
Release Status
Final
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Unknown
Created
12/28/2021 9:50:47 AM
Updated
12/28/2021 9:57:24 AM
Use Support
Class A1
Recreation - Primary contact
Not Assessed
Class BWW2
Aquatic Life - Warm Water Type 2
Not Supported
Support Level
Not Supported
Impairment Code
5b-v - Biological - verified
Cause Magnitude
Moderate
Status
Continuing
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
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class BWW2 use was assessed as “not supported” based on biological sampling data. All other designated uses were "not assessed."

Assessment Explanation

Data Sources:

Data Source

Data Source ID

Data Type

Data Age

Site ID

Site Name

Site Description

Iowa DNR

6

BIO

See Below

507

English Creek

Knoxville – REMAP #160


Presumptive Class A1 - No Data

Class BWW2 - Biological Sampling:

Benthic Macroinvertebrates:

BioNet Site ID

Date

Drainage Area (mi2)

Ecoregion

Major Drainage/Thermal

BM Sample Gear

BMIBI score

BMIBI Class

40a BMIBI BIT

BMIBI Pass/ Fail

507

8/14/14

74

40a

MS/WW

ArtSub

24

Poor

41

Fail

507

9/11/13

74

40a

MS/WW

ArtSub

22

Poor

41

Fail

507

8/1/13

74

40a

MS/WW

ArtSub

17

Poor

41

Fail


Fish:

BioNet Site ID

Date

Drainage Area (mi2)

Ecoregion

Major Drainage/Thermal

Riffle Stream?

FIBI score

FIBI Class

40a FIBI BIT

FIBI Pass/ Fail

507

8/14/14

74

40a

MS/WW

NA

17

Poor

33

Fail

507

9/11/13

74

40a

MS/WW

NA

0

Poor

33

Fail


Overall:

Community

Assessment Type

Assessment Result

Support Level

IR Category

Reason

Benthic Macroinvertebrates

Evaluated

Fail (0/3)

Not

Fish

Evaluated

Fail (0/2)

Not

Overall

Evaluated

Fail

Not

5bv

Assessment was evaluated because it included samples not collected in the last five years.


Class BWW2 – Continuous Monitoring Assessment:

Continuous monitoring data from 2013 and 2014 were examined for DO and stream temperature criteria violations. The lowest DO concentration recorded in 53 days of continuous monitoring was 2.3 mg/L. The daily DO minimum concentration failed to meet the 24-hour DO criterion (4 mg/L) in 4 of 53 days and the 16-hour DO criterion (5 mg/L) in 2 of 53 days. The 2013 and 2014 combined percentage exceeding the 24-hour DO criterion (7.5) was slightly less than (passing) the 10% impairment threshold used to assess conventional water quality parameters; however, the associated statistical analysis confidence level was not high (<90%). The 2013 and 2014 combined percentage exceeding the 16-hour DO criterion (3.8%) was less than (passing) the 10% impairment threshold; however, the associated statistical analysis confidence level was not high (<90%). The maximum stream temperature recorded during the sensor deployment period was 31.2 degrees (C). The temperature criterion for warmwater interior streams (32 C) was exceeded in 0 of 53 days. The percentage exceeding (0%) was less than (passing) the 10% impairment threshold with high statistical confidence (>90%). Based on these data, the BWW1 aquatic life use was assessed as not impaired by DO and temperature. The DNR’s continuous monitoring assessment methodology specifies that the frequency of violations must exceed the 10% threshold with greater than 90% statistical confidence in order to assess the aquatic life use as impaired. The assessment type is considered as “monitored” because the data meet the minimum requirements of the DNR’s continuous monitoring assessment methodology. Because of the contradictory results showing DO violations in the first year (2013) and not the second year of monitoring (2014), additional continuous monitoring of DO and temperature is strongly recommended.

Monitoring and Methods
Assessment Key Dates
7/3/2013
Non-fixed Monitoring Start Date
8/27/2014
Non-fixed Monitoring End Date
8/1/2013
Biological Monitoring
9/11/2013
Biological Monitoring
8/14/2014
Biological Monitoring
Methods
150
Monitoring data more than 5 years old
222
Non-fixed-station monitoring (conventional during key seasons and flows)
315
Regional reference site approach
320
Benthic macroinvertebrate surveys
330
Fish surveys