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
2016
Release Status
Final
Overall IR
3 - Insufficient data exist to determine whether any designated uses are met.
Trend
Unknown
Created
8/8/2016 10:21:59 AM
Updated
8/8/2016 10:21:59 AM
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
Agriculture
Source Confidence
Low
Cycle Added
2016
Impairment Rationale
Adverse impacts on plant/animal communities
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 B(LW) aquatic life uses are assessed (evaluated) as "not supported" due to high levels of algae at this wetland that suggest impairment due to aesthetically objectionable conditions. The fish consumption uses remain "not assessed" due to the lack of water quality information upon which to base an assessment. Sources of data for this assessment include results of water chemistry, aquatic vegetation, and fish monitoring conducted in 2012-2014 by the IDNR shallow lakes and wetland monitoring program and information from the IDNR Wildlife Bureau.

Assessment Explanation

Results of water quality monitoring conducted at Prairie Lake indicate that the aquatic life uses should be assessed (evaluated) as "not supported" due to high levels of algae at this lake.  This assessment is considered "evaluated" because only 5 samples were collected in 2014 during the current assessment period (2012-2014).   Based on IDNR's assessment methodology, 9 samples within the most recent three year period are necessary to accurately characterize water quality for the purposes of identifying impaired waters.  

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.  

Using the overall median values from the IDNR shallow lakes and wetlands monitoring program from 2012 through 2014 (approximately 5 samples), the median growing season total suspended solids concentration was 20 mg/L; this median value is well below the UMRCC guideline and suggests "full support" of the aquatic life uses.     

In addition, the level of algae, however, suggests "no support" of the aquatic life uses at Prairie Lake. The Carlson’s (1977) trophic state index value for chlorophyll a was 70. According to Carlson (1977), the index value for chlorophyll a places Prairie Lake in the eutrophic category.  This value suggests very high levels of chlorophyll a and suspended algae in the water and "evaluated/no support" of the aquatic life uses.

NOTE:  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 instance, water clarity may be sufficient to support the Class B(LW) 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.

Monitoring and Methods
Assessment Key Dates
5/13/2013
Fixed Monitoring Start Date
9/16/2013
Fixed Monitoring End Date
Methods
120
Surveys of fish and game biologists/other professionals
222
Non-fixed-station monitoring (conventional during key seasons and flows)
340
Primary producer surveys (phytoplankton/periphyton/macrophyton)