Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Marble Lake IA 06-LSR-1656

Dickinson County S17T100NR36W 3.5 mi. NE of Montgomery.

Cycle
2018
Release Status
Final
Overall IR
5 - Water is impaired or threatened and a TMDL is needed.
Trend
Stable
Created
6/13/2019 2:19:30 PM
Updated
6/13/2019 2:24:39 PM
Use Support
Class BLW
Aquatic Life - Lakes and wetlands
Not Supported
Support Level
Not Supported
Impairment Code
5* - 303(d)-impaired last cycle; fully supporting this cycle; potential de-listing.
Cause Magnitude
Slight
Status
Continuing
Source
Agriculture
Source Confidence
Low
Cycle Added
2014
Impairment Rationale
Adverse impacts on plant/animal communities
Data Source
Ambient monitoring: Iowa DNR-shallow lakes & wetlands
TMDL Priority
Tier IV
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 (monitored) 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 2014-2016 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 Marble Lake indicate that the aquatic life uses should be assessed (monitored) as "not supported" due to high levels of algae at this lake.

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 DNR shallow lakes and wetlands monitoring program from 2014 through 2016 (approximately 10 samples), the median growing season total suspended solids concentration was 14.1 mg/L; this median value is below the UMRCC guideline and suggests "full support" of the aquatic life uses.

In addition, the level of algae, however, suggests "full support" of the aquatic life uses at Marble Lake. The Carlson’s (1977) trophic state index value for chlorophyll a was 63. According to Carlson (1977), the index value for chlorophyll a places Marble Lake in the hypereutrophic category. This value suggests very high levels of chlorophyll a and suspended algae in the water and "no support" of the aquatic life uses.Based on DNR's methodology, the median TSI value for chlorophyll a must be 63 or less for two consecutive assessment/listing cycles before a lake can be removed from the state's Section 303(d) list (IR Category 5). Therefore, Lizard Lake will remain listed as "not supported" for the 2018 assessment/listing 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 instances, 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
5/19/2014
Fixed Monitoring Start Date
9/13/2016
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)