Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

South Twin Lake IA 04-RAC-1168

Calhoun County S1T88NR33W 3 mi N of Rockwell City.

This is a DRAFT assessment
Draft assessments may change without notice
Cycle
2026
Current Phase
Public Comment
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trophic
Hypereutrophic
Trend
Stable
Created
10/27/2025 3:11:39 PM
Updated
1/7/2026 1:48:30 PM
Use Support
Class BLW
Aquatic Life - Lakes and wetlands
Not Supported
Support Level
Not Supported
Impairment Code
5a - Pollutant-caused impairment. TMDL needed.
Cause Magnitude
Moderate
Status
Continuing
Source
Agriculture
Source Confidence
Moderate
Cycle Added
2010
Impairment Rationale
Adverse impacts on plant/animal communities
Data Source
Ambient monitoring: Iowa DNR-shallow lakes & wetlands
TMDL Priority
Tier IV
Support Level
Not Supported
Impairment Code
5a - Pollutant-caused impairment. TMDL needed.
Cause Magnitude
Moderate
Status
Continuing
Source
Agriculture
Source Confidence
Moderate
Cycle Added
2010
Impairment Rationale
Adverse impacts on plant/animal communities
Data Source
Ambient monitoring: Iowa DNR-shallow lakes & wetlands
TMDL Priority
Tier IV
Class HH
Human Health -
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class BLW use remains assessed (monitored) as "not supported" due to high levels of total suspended solids that leads to an impairment of the narrative criteria protecting against undesirable or nuisance aquatic life. High levels of algae at this shallow lake also suggested impairment due to aesthetically objectionable conditions. All other designated uses remain “not assessed.”

Assessment Explanation

  • Data Sources:

    Data Source

    Data Source ID

    Data Type

    Data Age

    Site ID

    Site Name

    Site Description

    Iowa DNR

    6

    WQ

    CY 2018-2021

    22130004

    South Twin Lake

    Class BLW – Shallow Lake TSI:

    Site ID

    Data Source ID

    Parameter Name

    # Samples / # Years

    Minimum Value

    Maximum Value

    Median Value

    Median TSI Violation?

    Assessment Type

    Support Level

    22130004

    6

    Chlorophyll a TSI

    35 / 4

    42

    90

    70

    YES

    MONITORED

    NOT

    The TSI value for Secchi depth is not used to evaluate the attainment of the aquatic life use in shallow lakes. Due to the depth of these shallow lakes, TSI values for Secchi depth can be misleading. In some instances, the Secchi disk remains visible at the bottom of the lake and the depth of the lake is recorded as the Secchi depth. In these instances, water clarity may be sufficient to support the Class BLW use, but the index value is limited by the depth of the lake. Thus, the combination of total suspended solids and chlorophyll a was used to determine whether or not the Class BLW use was impaired in these shallow systems.

    Class BLW - 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

    22130004

    6

    Dissolved Oxygen

    16 / 4

    7.5

    15.5

    10.1

    0

    NA / NA

    4

    NO

    MONITORED

    FULL

    22130004

    6

    pH

    11 / 3

    8.18

    8.98

    8.68

    0

    NA / NA

    3

    NO

    MONITORED

    FULL

    22130004

    6

    Temperature

    16 / 4

    14.6

    28.8

    22.8

    0

    NA / NA

    4

    NO

    MONITORED

    FULL

    Class BLW - Protection of Submerged Aquatic Vegetation:

    Site ID

    Data Source ID

    Parameter Name

    # Samples / # Years

    Minimum Value

    Maximum Value

    Median Value

    Median Value >= SAV

    Assessment Type

    Support Level

    22130004

    6

    Total suspended solids

    33 / 4

    23

    470

    66

    YES

    MONITORED

    NOT

    Guidelines for wetland assessment from the Upper Mississippi River Conservation Committee’s Water Quality Technical Section (2003) state that a median total suspended solids concentration during the growing season of less than 30 mg/L is necessary to provide sufficient water clarity to support the growth of submersed aquatic vegetation (SAV) in wetlands and shallow lakes. High levels of total suspended solids impede the growth of SAV. SAV is critical to the health of wetland and shallow lake ecosystems. The elimination of SAV can degrade habitat quality such that undesirable aquatic species such as cyanobacteria, common carp and fathead minnows dominate. As such, the suppression of SAV constitutes a violation of Iowa’s narrative water quality criteria protecting against undesirable or nuisance aquatic life.

    Class BLW - 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

    22130004

    6

    Ammonia

    5 / 1

    0.025

    0.02

    0.02

    0 / 0

    NO

    EVALUATED

    FULL

    Class HH - No Data

    Additional Notes:

    Additional monitoring of fish and aquatic vegetation populations at South Twin Lake by DNR staff also suggests that the high levels of total suspended solids and algae have adverse effects on fish populations and limit the production of rooted aquatic vegetation in this wetland. These results further indicate that the aquatic life uses of this wetland should be assessed as "not supported."

    According to the local DNR Wildlife Biologist (Mahn), siltation at South Twin Lake is a problem but probably not a serious one because (1) the wetland has a rather small watershed and (2) most of the contributing watershed comes from the outlet of North Twin Lake and contains relatively little silt. The majority of the land immediately surrounding South Twin Lake, however, is intensively farmed and thus contributes to a siltation problem. Some progress has been made on the north side of the lake on private property with the establishment of grass that reduces silt. DNR has purchased a small tract on the southwest side of the lake that includes a small wetland and some adjacent uplands which have been seeded to native grasses. The primary water quality problems at South Twin Lake are increased turbidity, reduced light penetration, suppressed aquatic vegetation, and an accelerated eutrophication of this wetland. A large populations of common carp population exists in the wetland and no doubt plays a significant role in the turbidity problem and the suppression of rooted aquatic vegetation.

Monitoring and Methods
Assessment Key Dates
5/10/2018
Monitoring Start
6/24/2021
Monitoring End
Methods
120
Surveys of fish and game biologists/other professionals
200
Physical/Chemical Monitoring
340
Primary producer surveys (phytoplankton/periphyton/macrophyton)