Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Lake Odessa IA 01-NEM-65

Louisa County S2T73NR2W 4 mi. E of Wapello.

Assessment Cycle
2014
Result Period
2010 - 2012
Designations
Class B(LW) Class A1 Class HH
Assessment Methodology
Assessment Type
Evaluated
Integrated Report
Category 3b
Trend
Unknown
Legacy ADBCode
IA 01-NEM-00105-L_0
Overall Use Support
Partial
Aquatic Life Use Support
Fully
Fish Consumption
Not assessed
Primary Contact Recreation
Partial
Documentation
Assessment Comments

Assessment is based on monitoring conducted in 2006 and 2007.

Basis for Assessment

SUMMARY:  The Class B(LW) aquatic life uses are assessed (evaluated) as "partially supported" (IR Category 3b) due to 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 wetland 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 monitoring collected by IDNR in 2006 and 2007 and information from the IDNR Wildlife Bureau.  

EXPLANATION:  Results of water quality monitoring conducted at Lake Odessa indicate that the aquatic life uses should be assessed (evaluated) as "partially supported" due to high levels of total suspended solids and algae at this lake.    This assessment is considered "evaluated" because only 6 samples were collected between 2006 and 2007.    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.   This waterbody will be added to Iowa's list of waters in need of further investigation.  

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 2006/2007 (approximately 6 samples), the median growing season total suspended solids concentration was 71.5 mg/L; this median value exceeds the UMRCC guideline.    Thus, based on (1) suppression of SAV growth, (2) the resultant production of undesirable aquatic life, and (3) IDNR’s assessment and listing methodology, the aquatic life uses at Lake Odessa are assessed as “not supported” due to high levels of total suspended solids.  

In addition, the level of algae also suggests impairment of the aquatic life uses at Lake Odessa.    The Carlson’s (1977) trophic state index value for chlorophyll a was 81.     According to Carlson (1977), the index value for chlorophyll a places Lake Odessa in the hypereutrophic category.     This value suggests extremely high levels of chlorophyll a and suspended algae in the water.      

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.  

Fish Consumption uses remain "not assessed" as no monitoring data have been collected on which to base an assessment.

Monitoring and Methods
Assessment Key Dates
8/6/2007 Fixed Monitoring End Date
6/6/2006 Fixed Monitoring Start Date
Methods
120 Surveys of fish and game biologists/other professionals
Monitoring Levels
Biological 0
Habitat 0
Physical Chemistry 2
Toxic 0
Pathogen Indicators 0
Other Health Indicators 0
Other Aquatic Life Indicators 0
# of Bio Sites 0
BioIntegrity N/A
Causes and Sources of Impairment
Causes Use Support Cause Magnitude Sources Source Magnitude
Nutrients Aquatic Life Support Not Impairing
  • Agriculture
  • Natural Sources
  • Not Impairing
  • Not Impairing
Flow alteration Aquatic Life Support Not Impairing
  • Flow Regulation/Modification
  • Not Impairing