Iowa DNR
Iowa DNR

ADBNet

Water Quality Assessments
Impaired Waters List

Barringer Slough IA 06-LSR-1631

Clay County S14T96NR35W 4 mi ENE of Dickens.

Overall IR
3 - Insufficient data exist to determine whether any designated uses are met.
Trend
Unknown
Created
7/22/2016 8:18:42 AM by
Updated
7/22/2016 8:18:42 AM by
Use Support
Class BLW
Aquatic Life - Lakes and wetlands
WINOFI
Impairment Code
3b - Use potentially impaired based on an evaluated assessment.
Cause Magnitude
Slight
303(d) Listing Status
Continuing
Source
Agriculture
Source Confidence
Moderate
Cycle Added
2012
Impairment Rationale
Adverse impacts on plant/animal communities
Data Source
Ambient monitoring: Iowa DNR-shallow lakes & wetlands
Impairment Code
3b - Use potentially impaired based on an evaluated assessment.
Cause Magnitude
Moderate
303(d) Listing Status
Continuing
Source
Other: Sediment Resuspension
Source Confidence
Low
Cycle Added
2012
Impairment Rationale
Adverse impacts on plant/animal communities
Data Source
Ambient monitoring: Iowa DNR-shallow lakes & wetlands
Impairment Code
3b - Use potentially impaired based on an evaluated assessment.
Cause Magnitude
Slight
303(d) Listing Status
Continuing
Source
Other: Sediment Resuspension
Source Confidence
Low
Cycle Added
2002
Impairment Rationale
Adverse impacts on plant/animal communities
Data Source
Biological monitoring: Iowa DNR Fisheries
Class HH
Human Health -
Not Assessed
General Use
General Use water -
Not Assessed
No delistings for this assessment cycle.
Documentation
Assessment Summary

The Class B(LW) aquatic life uses are assessed (evaluated) as "not supported" due to poor water clarity caused by 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 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 quality, aquatic vegetation, and fish monitoring conducted by the IDNR shallow lakes and wetlands monitoring program from 2012 through 2014 and information from the IDNR Wildlife Bureau.

Assessment Explanation

Results of water quality monitoring conducted at Barringer Slough indicate that the aquatic life uses should be assessed (evaluated) as "not supported" due to high levels of total suspended solids, algae, and turbidity 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 4 mg/L; this median value is well below the UMRCC guideline and suggests "full support" of the aquatic life uses. While this assessment is assessed as "evaluated/full support", the previous assessment for the aquatic life uses at Barringer Slough was assessed as “not supported” due to high levels of total suspended solids. Therefor, Barringer Slough will remain assessed as “not supported” due to high levels of total suspended solids for the 2016 assessment cycle.

In addition, the level of algae also suggests "full support" of the aquatic life uses at Barringer Slough. The Carlson’s (1977) trophic state index value for chlorophyll a was 54. According to Carlson (1977), the index value for chlorophyll a places Barringer Slough in the eutrophic category.  This value suggests low levels of chlorophyll a and suspended algae in the water and "full support" of the aquatic life uses. While this assessment is assessed as "evaluated/full support", the previous assessment for the aquatic life uses at Barringer Slough was assessed as “not supported” due to the index value for chlorophyll a suggesting extremely high levels of chlorophyll a and suspended algae in the water.  Therefor, Barringer Slough will remain assessed as “not supported” due to High levels of algae (Chlorophyll a) for the 2016 assessment cycle.

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.

Additional monitoring of fish and aquatic vegetation populations at Barringer Slough by IDNR 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."

Monitoring and Methods
Assessment Key Dates
5/20/2014
Fixed Monitoring Start Date
9/15/2014
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)