Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Prairie Lake IA 06-LSR-1647

Dickinson County S23T99NR36W 3.5 mi. SE of Spirit Lake.

Cycle
2020
Release Status
Final
Overall IR
3 - Insufficient data exist to determine whether any designated uses are met.
Trend
Unknown
Created
8/27/2020 2:47:29 PM
Updated
10/13/2020 2:08:26 PM
Use Support
Class BLW
Aquatic Life - Lakes and wetlands
WINOFI
Impairment Code
3b - Use potentially impaired based on an evaluated assessment.
Cause Magnitude
Moderate
Status
New
Source
Unknown: Source Unknown
Source Confidence
N/A
Cycle Added
2020
Impairment Rationale
Significantly > 10% of samples fail to meet criterion
Data Source
Ambient monitoring: Iowa DNR-shallow lakes & wetlands
Class HH
Human Health -
Not Assessed
General Use
General Use water -
Not Assessed
Impairment Delistings
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class BLW use is assessed as "not supported" due to violations of the Class BLW criterion for pH. All other designated uses are “not assessed”.

Assessment Explanation

Sources of Data:

Data Source

Data Source ID

Data Type

Data Age

Site ID

Site Name

Site Description

Iowa DNR

6

WQ

CY 2016-2018

22300021

Prairie Lake


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

22300021

6

Chlorophyll a TSI

10 / 2

24

82

57

NO

Assessor Discretion

Full

22300021

6

Total Phosphorus TSI

10 / 2

50

85

61

NA

NA

NA

22300021

6

Inorganic suspended solids

10 / 2

0

71.5

4.1

NA

NA

NA

  • The TSI value for Secchi depth is not used to evaluate the attainment of aquatic life goals 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 B(LW) uses are impaired in these shallow systems.

Class BLW - Conventional Parameters:

Site ID

Data Source ID

Parameter Name

# Samples / # Years

Maximum Value

Mean Value

Median Value

# Acute / Chronic Violations

% Acute/ Chronic Violations

Significantly >10% Violations

Assessment Type

Support Level

22300021

6

Ammonia

5 / 1

0.3244

0.13

0.08

0 / 2

0% / 40%

NO

Evaluated

Full

22300021

6

Dissolved oxygen

5 / 1

9.7

8.4

8

NA / 0

NA / 0%

NO

Evaluated

Full

22300021

6

pH

5 / 1

12.08

10.73

10.3

5 / NA

100% / NA

YES

Evaluated

Not

22300021

6

Temperature

5 / 1

24.7

21.7

22.7

0 / 0

0% / 0%

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

22300021

6

Total suspended solids

10 / 2

1.4

186.5

8.9

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

Monitoring and Methods
Assessment Key Dates
5/18/2016
Fixed Monitoring Start Date
9/11/2018
Fixed Monitoring End Date
Methods
220
Non-fixed station physical/chemical monitoring (conventional pollutant only)