Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Green Castle Lake IA 02-IOW-643

Marshall County S8T82NR17W 1 mi. S of Ferguson.

Cycle
2016
Release Status
Final
Overall IR
3 - Insufficient data exist to determine whether any designated uses are met.
Trophic
Eutrophic
Trend
Unknown
Created
5/26/2016 11:30:40 AM
Updated
8/1/2016 2:17:13 PM
Use Support
Class A1
Recreation - Primary contact
WINOFI
Impairment Code
3b - Use potentially impaired based on an evaluated assessment.
Cause Magnitude
Slight
Status
New
Source
Other: Sediment Resuspension
Source Confidence
Low
Cycle Added
2016
Impairment Rationale
Narrative criteria violation: aesthetically objectionable conditions
Data Source
Ambient monitoring: Iowa DNR-lakes
Class BLW
Aquatic Life - Lakes and wetlands
Fully Supported
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 A1 (primary contact recreation) uses are assessed (evaluated) as "partially supported" due to poor water transparency. The Class B(LW) (aquatic life) uses are assessed (monitored) as “fully supported.” Fish consumption uses remain “not assessed.” Note: For the 2010 assessment/listing cycle, Green Castle Lake was listed as "partially supporting" due to high levels of pH that violated the state criterion. Sources of data for this assessment include (1) results of the statewide survey of Iowa lakes conducted from 2010 through 2014 by Iowa State University (ISU), and (2) information from the IDNR Fisheries Bureau.

Assessment Explanation

For the 2016 assessment/listing cycle, the Class A1 (primary contact recreation) uses of Green Castle Lake are assessed (evaluated) as "partially supported" due to poor water transparency based on information from the ISU lake survey. Using the median values from these surveys from 2010-2012 (approximately 9 samples), Carlson 's (1977) trophic state indices for Secchi depth, chlorophyll a, and total phosphorus were 67, 63, and 61 respectively for Green Castle Lake. According to Carlson (1977) the Secchi depth, chlorophyll a, and total phosphorus values all place Green Castle Lake in the Eutrophic category. These values suggest moderately high levels of chlorophyll a and suspended algae in the water, poor water transparency, and moderately high levels of phosphorus in the water column. The data show no violations of the Class A1 criterion for pH in 9 samples. This assessment of "evaluated/partially supported" is due to the lack of data during this assessment cycle to justify an impairment. The lake was drawn down during this assessment cycle.

The level of inorganic suspended solids was moderately high at Green Castle Lake, and does suggest that non-algal turbidity may contribute to the impairment at this lake. The median level of inorganic suspended solids in Green Castle Lake (6 mg/L) was ranked 95th among the 138 lakes by the ISU lake survey.

Data from the 2010-2012 ISU lake survey suggest a moderate population of cyanobacteria exists at Green Castle Lake. These data show that cyanobacteria comprised 83% of the phytoplankton wet mass at this lake. The median cyanobacteria wet mass (13.3 mg/L) was ranked 41st of the 138 lakes sampled.

The Class B(LW) (aquatic life) uses are assessed (evaluated) as "fully supported." Results of the ISU lake survey from 2010-2012 show there were no violations of the criterion for ammonia in 9 samples(0%), no violations of the criterion for dissolved oxygen in 9 samples(0%), and no violations of the criterion for pH in 9 samples(0%). Based on IDNR's assessment methodology these violations are not significantly greater than 10% of the samples and therefore suggest (fully supported/evaluated) of the Class B(LW) uses of Green Castle Lake.

Fish consumption uses remain "not assessed" due to the lack of fish contaminant monitoring in this lake.

Note: Green Castle Lake was drained in 2013. Common carp and silt were removed from the lake and fish habitat improvements were made. Improvements in water clarity were observed in 2015 sampling season after the lake refilled.

Monitoring and Methods
Assessment Key Dates
6/21/2010
Fixed Monitoring Start Date
9/19/2012
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)