Iowa DNR
ADBNet

Water Quality Assessments

Impaired Waters List

Maquoketa River IA 01-MAQ-14

from N. Fk. Maquoketa R. to confluence with Farm Cr. in S10 T85N R1W Jones Co.

Assessment Cycle
2022
Release Status
Final
Data Collection Period
Overall IR Category
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Unknown
Created
12/6/2021 3:06:16 PM
Updated
1/12/2022 2:35:35 PM
Assessment conducted in accordance with Iowa's 2022 IR methodology
Use Support
Class A1
Not Supported
Bacteria: Indicator Bacteria- E. coli
Support Level
Not Supported
Impairment Code
4a - Pollutant-caused impairment. TMDL has been completed.
Cause Magnitude
Slight
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2002
Impairment Rationale
Geometric mean criterion exceeded
Data Source
Ambient monitoring: Iowa DNR-rivers
Class BWW1
Not Supported
Biological: loss of native mussel species
Support Level
Not Supported
Impairment Code
5b - Biological impairment or pollutant-caused fish kill - unknown source. No administrative action.
Cause Magnitude
High
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2004
Impairment Rationale
Loss of >50% of native mussel species
Data Source
Biological monitoring: Iowa DNR freshwater mussels
TMDL Priority
Tier IV
Biological: low aquatic macroinvertebrate IBI
Support Level
Water in Need of Further Investigation (WINOFI)
Impairment Code
3b-u - Use potentially biologically impaired based on uncalibrated IBI metrics.
Cause Magnitude
Slight
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
Low
Cycle Added
2016
Impairment Rationale
Low Biotic Index
Data Source
Biological monitoring: Iowa DNR WQMA
Class HH
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class A1 use was assessed as "not supported" due to levels of indicator bacteria (E. coli) that exceeded state water quality criteria. The Class BWW1 use was assessed as "not supported" due the apparent elimination of the freshwater mussel community from this river segment. All other designated uses were "not assessed." Note: A TMDL for pathogen indicators in this segment of the Maquoketa River was prepared by DNR and approved by EPA in 2006.

Assessment Explanation

Data Sources:

Data Source

Data Source ID

Data Type

Data Age

Site ID

Site Name

Site Description

Iowa DNR

6

WQ

CY 2018-2020

10490004

Maquoketa River west of Maquoketa

Iowa DNR

6

BIO

See Below

381

Maquoketa River

Canton – REMAP #62

Iowa DNR

6

BIO

See Below

1151

Maquoketa River

0.9 mi upstream of Hwy 61 bridge - Maquoketa


Class A1 - Indicator Bacteria:

Site ID

Data Source ID

# Samples per Year (2018/ 2019/2020)

2018 Geometric Mean

2019 Geometric Mean

2020 Geometric Mean

Violates Annual Geometric Mean?

# 2018 SSM violations / SSM Violations needed for impairment

# 2019 SSM violations / SSM Violations needed for impairment

# 2020 SSM violations / SSM Violations needed for impairment

Violates Annual SSM Significantly >10% Rule?

Assessment Type

Support Level

10490004

6

7/7/8

883

1399

728

YES

6 / 3

5 / 3

5 / 3

YES

Monitored

Not


Class A - pH

Site ID

Data Source ID

# Samples / # Years

Minimum Value

Maximum Value

Mean Value

# Violations

Violations needed for impairment

Violates Significantly >10% Rule?

Assessment Type

Support Level

10490004

6

36 / 3

7.3

8.4

8.1

0

7

NO

Monitored

Full


Class BWW1 - Conventional Parameters:

Site ID

Data Source ID

Parameter Name

# Samples / # Years

Minimum Value

Maximum Value

Mean Value

# Violations

# Acute / Chronic Violations

Violations needed for impairment

Violates Significantly >10% Rule?

Assessment Type

Support Level

10490004

6

Ammonia

36 / 3

0.02

0.43

0.08

NA

0 / 0

7

NO

Monitored

Full

10490004

6

Chloride

36 / 3

8.2

23

17.7

NA

0 / 0

7

NO

Monitored

Full

10490004

6

Dissolved Oxygen

36 / 3

7.6

13.5

11

0

NA / NA

7

NO

Monitored

Full

10490004

6

pH

36 / 3

7.3

8.4

8.1

0

NA / NA

7

NO

Monitored

Full

10490004

6

Sulfate

36 / 3

8.7

26

19

0

NA / NA

7

NO

Monitored

Full

10490004

6

Temperature

36 / 3

0.1

27.1

12.1

0

NA / NA

7

NO

Monitored

Full


Class BWW1 - Toxic Parameters:

Site ID

Data Source ID

Parameter Name

# Samples / # Years

Maximum Value

Mean Value

Median Value

# Acute / Chronic Violations

>1 Acute / Chronic Violation

Assessment Type

Support Level

10490004

6

Aluminum

14 / 3

1.7

0.7

0.3

0 / 0

NO

Monitored

Full

10490004

6

Arsenic

13 / 3

0.96

0.66

0.66

0 / 0

NO

Monitored

Full

10490004

6

Cadmium

13 / 3

0.07

0.03

0.02

0 / 0

NO

Monitored

Full

10490004

6

Chromium

13 / 3

1.2

1

1

0 / 0

NO

Monitored

Full

10490004

6

Lead

13 / 3

0.47

0.14

0.11

0 / 0

NO

Monitored

Full

10490004

6

Nickel

13 / 3

3.5

2.5

2.5

0 / 0

NO

Monitored

Full

10490004

6

Silver

13 / 3

0.025

0.025

0.025

0 / 0

NO

Monitored

Full

10490004

6

Zinc

13 / 3

5.3

2

1.8

0 / 0

NO

Monitored

Full


Class BWW1 - Biological Sampling:


Benthic Macroinvertebrates:

Site ID

Date

Drainage Area (mi2)

Ecoregion

Major Drainage

BM Sample Gear

BMIBI score

BMIBI Class

47f BMIBI BIT

BMIBI Pass/ Fail

381

10/13/20

754

47f

MS

Floating Art Sub

59

Good

51

Pass

1151

9/11/17

950

47f

MS

Hess

40

Fair

51

Fail


Overall:

Community

Assessment Type

Assessment Result

Support Level

IR Category

Reason

Benthic Macroinvertebrates

Evaluated

Fail (1/2)

Not

Assessment was evaluated because the drainage areas of the sample sites

Overall

Evaluated

Fail

WINOFI

3bu

were greater than the calibrated range.


Class BWW1 – Freshwater Mussel Sampling:

Freshwater Mussel Survey

# Freshwater Mussel Species

# Freshwater Mussel Species Increase/Decrease

% Freshwater Mussel Species Increase/Decrease

Assessment Type

Support Level

IR Category

1984-85 (Frest 1987)

5

1998-99 (Arbuckle et al. 2000)

0

-5

-100%

Evaluated

Not

5b

As presented by Arbuckle et al. (2000), the potential causes of declines in species richness of Iowa's freshwater mussels include siltation, destabilization of stream substrate, stream flow instability, and high instream levels of nutrients (phosphorus and nitrogen). Their study also suggested the importance of stream shading provided by riparian vegetation to mussel species richness.


Class HH - No Data

Monitoring and Methods
Assessment Key Dates
9/30/1985 Biological Monitoring
9/30/1999 Biological Monitoring
1/9/2018 Fixed Monitoring Start Date
12/1/2020 Fixed Monitoring End Date
9/11/2017 Biological Monitoring
10/13/2020 Biological Monitoring
6/1/2006 TMDL Completed
Methods
150 Monitoring data more than 5 years old
230 Fixed station physical/chemical (conventional plus toxic pollutants)
315 Regional reference site approach
320 Benthic macroinvertebrate surveys
420 Indicator bacteria monitoring