Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Garlock Slough IA 06-LSR-1654

Dickinson County S35T99NR37W 2.5 mi. NW of Milford.

Cycle
2022
Release Status
Final
Overall IR
3 - Insufficient data exist to determine whether any designated uses are met.
Trend
Stable
Created
1/4/2022 10:44:07 AM
Updated
2/17/2022 2:51:36 PM
Use Support
Class BLW
Aquatic Life - Lakes and wetlands
WINOFI
Impairment Code
3b - Use potentially impaired based on an evaluated assessment.
Cause Magnitude
Slight
Status
New
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2022
Impairment Rationale
Potential Impairment
Data Source
Ambient monitoring: Iowa DNR-shallow lakes & wetlands
Class HH
Human Health -
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class BLW use was assessed (evaluated) as "WINOFI" due to violations in the class BLW criteria for dissolved oxygen. 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

    WQ

    CY 2017-2018

    14000183

    Garlock Slough

    Class BLW - TSI's

    Site ID

    Data Source ID

    Parameter Name

    # Samples / # Years

    Minimum Value

    Maximum Value

    Median Value

    Median TSI Violation?

    Assessment Type

    Support Level

    14000183

    6

    Chlorophyll a TSI

    10 / 2

    24

    83

    52

    NO

    Evaluated

    Full

    14000183

    6

    Total Phosphorus TSI

    10 / 2

    61

    105

    72

    NA

    NA

    NA

    14000183

    6

    Inorganic suspended solids

    10 / 2

    0.06

    17

    9

    NA

    NA

    NA

    The TSI value for Secchi depth is not used to evaluate the attainment of 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 uses, but the index value is limited by the depth of the lake. Thus the combination of total suspended solids and chlorophyll a will be used to determine whether or not the Class BLW uses are impaired in these shallow systems.

    Class BLW - 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

    14000183

    6

    Dissolved Oxygen

    7 / 2

    1.26

    5.24

    3.65

    5

    NA / NA

    3

    YES

    Evaluated

    WINOFI

    14000183

    6

    pH

    7 / 2

    7.39

    8.74

    7.8

    0

    NA / NA

    3

    NO

    Evaluated

    Full

    14000183

    6

    Temperature

    7 / 2

    17.92

    25.89

    22.15

    0

    NA / NA

    3

    NO

    Evaluated

    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

    14000183

    6

    Total suspended solids

    10 / 2

    0.5

    83

    10.8

    NO

    Monitored

    Full

    Guidelines for wetland assessment from the Upper Mississippi River Conservation Committee’s Water Quality Technical Section (2003) state that an average 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 in wetlands and shallow lakes. High levels of total suspended solids impede the growth of submersed aquatic vegetation (SAV). Submersed aquatic vegetation 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 HH - No Data

    In general, Iowa wetlands are not managed for recreational fisheries; thus, fish contaminant monitoring is not typically conducted at these waterbodies.

Monitoring and Methods
Assessment Key Dates
5/16/2017
Fixed Monitoring Start Date
9/11/2018
Fixed Monitoring End Date
Methods
222
Non-fixed-station monitoring (conventional during key seasons and flows)