Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Des Moines River IA 04-UDM-1212

from the Interstate 80/35 bridge (S17 T79N R24W Polk Co.) to Saylorville Dam in S30 T80N R24W Polk Co.

This is a DRAFT assessment
Draft assessments may change without notice
Cycle
2026
Current Phase
Public Comment
Overall IR
2 - Some of the designated uses are met but there is insufficient data to determine if remaining designated uses are met.
Trend
Stable
Created
10/27/2025 3:09:49 PM
Updated
2/3/2026 2:07:44 PM
Use Support
Class A1
Recreation - Primary contact
Fully Supported
Class BWW1
Aquatic Life - Warm Water Type 1
WINOFI
Impairment Code
3b-u - Use potentially biologically impaired based on uncalibrated IBI metrics.
Cause Magnitude
Moderate
Status
Continuing
Source
Unknown: Source Unknown
Source Confidence
Low
Cycle Added
2014
Impairment Rationale
Potential Impairment
Data Source
Biological monitoring: Iowa DNR WQMA
Impairment Code
3b - Use potentially impaired based on an evaluated assessment.
Cause Magnitude
Slight
Status
New
Source
Hydromodification: Flow Regulation/Modification
Source Confidence
Low
Cycle Added
2026
Impairment Rationale
Potential Impairment
Data Source
Fish kill investigation: Iowa DNR
Class C
Drinking Water -
Fully Supported
Class HH
Human Health -
Fully Supported
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class A1 use was assessed as "fully supported" based on indicator bacteria and pH monitoring. The Class BWW1 use was assessed as "WINOFI” based on biological sampling data and the occurrence of a single fish kill. The Class C (drinking water) use was assessed as "fully supported" based on water quality monitoring data. The Class HH (fish consumption) use was assessed as "fully supported" based on fish tissue sampling data. Note: A TMDL for the nitrate impairment in this segment was approved by EPA in September 2009. The TMDL covered the nitrate impairment identified for this segment and the impairment remained in IR Category 4a (impaired; TMDL approved) until the 2022 IR cycle. However, the nitrate monitoring data collected since then has indicated "full support."

Assessment Explanation

Data Sources:

Data Source

Data Source ID

Data Type

Data Age

Site ID

Site Name

Site Description

USACE

12

WQ

CY 2022-2024

17770001

Des Moines River at 66th. St.

USACE

12

FT

See Below

17770001

Des Moines River at 66th. St.

Iowa DNR

6

BIO

See Below

917

Des Moines River

Des Moines – US1


Class A1 - Indicator Bacteria:

Site ID

Data Source ID

# Samples per Year (2022/ 2023/2024)

2022 Geometric Mean

2023 Geometric Mean

2024 Geometric Mean

Violates Annual Geometric Mean?

# 2022 SSM violations / SSM Violations needed for impairment

# 2023 SSM violations / SSM Violations needed for impairment

# 2024 SSM violations / SSM Violations needed for impairment

Violates Annual SSM Significantly >10% Rule?

Assessment Type

Support Level

17770001

12

10/10/10

16

23

12

NO

0 / 3

1 / 3

0 / 3

NO

MONITORED

FULL


Class A1 – 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

17770001

12

67 / 3

7.81

9.01

8.21

1

11

NO

MONITORED

FULL


Class BWW1 - Binomial 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

17770001

12

Dissolved Oxygen

67 / 3

8.15

15.46

11.13

0

NA / NA

11

NO

MONITORED

FULL

17770001

12

pH

67 / 3

7.81

9.01

8.21

1

NA / NA

11

NO

MONITORED

FULL

17770001

12

Temperature

67 / 3

1.4

29.4

17

0

NA / NA

11

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

17770001

12

Ammonia

60 / 3

0.43

0.13

0.09

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

47b BMIBI BIT

BMIBI Pass/Fail

917

9/17/14

5840

47b

MS

Floating Art Sub

29

Poor

62

Fail


Overall:

Community

Assessment Type

Assessment Result

Support Level

IR Category

Reason

Benthic Macroinvertebrates

Evaluated

Fail (0/1)

WINOFI

Assessment was evaluated because the drainage area

Overall

Evaluated

Fail

WINOFI

3bu

of the site is greater than the calibrated range.


Class BWW1 - Fish kill Assessment:

A July 2024 fish kill occurred in the Des Moines River immediately downriver from the Saylorville dam that was caused by gas bubble trauma (GBT). Fish kills caused by GBT occur due to a large imbalance between the concentrations of atmospheric gasses in the water and the levels of these gasses dissolved in the blood of the fish. The concentrations of dissolved gasses such as oxygen and nitrogen in river water tend to equal the concentrations in the blood of a fish. When the levels of atmospheric gasses dissolved in river water become very high (i.e., super-saturated)—such as can happen when water moves through or over a large dam—the levels of these gasses will also rise in the blood of fish. As long as fish can stay in deeper water, the hydrostatic (water) pressure will keep these gasses fully dissolved in the fish’s blood. If, however, the flow of water downstream from the dam is decreased suddenly, the depth of the water will also decrease. With shallower water, fish are not able to move to deeper areas to keep the hydrostatic pressure sufficiently high to keep the gasses fully dissolved in their blood. During these conditions, the gasses dissolved in the fish’s blood will gradually come out of solution as bubbles, and these bubbles will interfere with blood circulation. Symptoms of gas bubble trauma in fish include gas blisters on the skin at the margins of the scales and as pop-eye (exophthalmia) where the eyes of the fish distend from the eye sockets. In the extreme case, blood circulation is disrupted to the point that fish kills occur.

The aquatic life use was placed in Category 3b (WINOFI list – potential impairment) because there weren’t multiple fish kills in this segment in the last five years. Should additional GBT fish kills occur in this segment in the future, the aquatic life use will be moved to IR Category 5b and be placed on the Impaired Waters List.

Details about the 2024 fish kill can be found here: https://programs.iowadnr.gov/fishkill/events/1059


Class C - Binomial Parameters:

Site ID

Data Source ID

Parameter Name

# Samples / # Years

Minimum Value

Maximum Value

Mean Value

Median Value

# Violations

Violates Significantly >10% Rule?

Assessment Type

Support Level

17770001

12

Inorganic nitrogen (nitrate and nitrite)

58 / 3

0.3

15.4

3.6

2.3

5

NO

MONITORED

FULL

17770001

12

pH

67 / 3

7.81

9.01

8.21

8.18

1

NO

MONITORED

FULL


Class HH - Fish Tissue Sampling:

Site ID

Biopart

Year

Species

# in sample / # of samples

Avg Length (cm)

(Avg) Hg (ppm)

Chlordane (ppm)

Sum PCBs (ppm)

17770001

whole

2016

common carp

5

NA

NA

0.03

<0.06

17770001

fillet

2016

largemouth bass

2

NA

0.11

Support Level

Full

Evaluated



Monitoring and Methods
Assessment Key Dates
9/17/2014
Biological Monitoring
12/2/2024
Monitoring End
1/4/2022
Monitoring Start
6/1/2016
Fish Tissue Monitoring
9/1/2009
TMDL Completed
7/26/2024
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
200
Physical/Chemical Monitoring
260
Fish tissue analysis
315
Regional reference site approach
320
Benthic macroinvertebrate surveys
420
Indicator bacteria monitoring
860
Other Agencies/Organizations provided monitoring data