Iowa DNR
Iowa DNR
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Water Quality Assessments
Impaired Waters List

Lake Smith IA 04-EDM-981

Kossuth County S36T96NR29W 3 mi. N of Algona.

Assessment Cycle
2010
Result Period
2006 - 2008
Designations
Class B(LW) Class A1 Class HH
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 4a
Trophic
Eutrophic
Trend
Stable
Legacy ADBCode
IA 04-EDM-00610-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: (1) results of the statewide survey of Iowa lakes conducted from 2004 through 2007 by Iowa State University (ISU), (2) results of the statewide ambient lake monitoring program conducted from 2005 through 2008 by University Hygienic Laboratory (UHL), and (3) information from the IDNR Fisheries Bureau.

Basis for Assessment

SUMMARY: The Class A1 (primary contact recreation) uses are assessed (monitored) as “partially supported” due to high levels of algae (chlorophyll a) and poor water clarity.   The Class B(LW) (aquatic life) uses are assessed (monitored) as “fully supported.”  Fish consumption uses are “not assessed” due to a lack of information upon which to base an assessment.   Sources of data for this assessment include (1) results of the statewide survey of Iowa lakes conducted from 2004 through 2007 by Iowa State University (ISU), (2) results of the statewide ambient lake monitoring program conducted from 2005 through 2008 by University Hygienic Laboratory (UHL), and (3) information from the IDNR Fisheries Bureau.

Note:  A TMDL for noxious aquatic plants at Lake Smith was prepared by IDNR and approved by EPA in 2005.   The basis of the impairment at this lake was high populations of cyanobacteria (=noxious aquatic plants).   Based on recent monitoring, a fish kill in the winter of 2000-01 and a subsequent lake renovation has significantly decreased the amount of cyanobacteria in this lake.   Recent ISU and UHL lake monitoring data strongly suggest that the impairment due to noxious aquatic plants (cyanobacteria) no longer exists.   Non-cyanobacteria algal populations, however, remain elevated at this lake and suggest "partial support" of the Class A1 uses.   Because algae populations are addressed in the TMDL this lake is placed in IR Category 4a (impaired; TMDL approved) for the 2010 cycle.

EXPLANATION: Results from the ISU and UHL lake surveys suggest that the Class A1 uses at Lake Smith are “partially supported” due to high levels of algae and poor water clarity.   Using the median values from these surveys from 2004 through 2008 (approximately 19 samples), Carlson’s (1977) trophic state indices for Secchi depth, chlorophyll a, and total phosphorus were 67, 68, and 74 respectively for Lake Smith.   According to Carlson (1977) the Secchi depth and chlorophyll a values place Lake Smith in between the eutrophic and hypereutrophic categories, while the total phosphorus value places Lake Smith in the hypereutrophic category.   These values suggest high levels of chlorophyll a and suspended algae in the water, poor water transparency, and very high levels of phosphorus in the water column.  

The level of inorganic suspended solids is moderately high at this lake but does not suggest impairment due to high non-algal turbidity.   The median inorganic suspended solids concentration at Lake Smith was 4.1 mg/L, which was the 61st highest of the 132 monitored lakes.

Data from the 2004-2008 ISU and UHL surveys suggest a very small population of cyanobacteria exists at Lake Smith, which does not suggest impairment at this lake due to noxious aquatic plants.   These data show that cyanobacteria comprised only 7% of the phytoplankton wet mass at this lake.   The median cyanobacteria wet mass (2.1 mg/L) was the 10th lowest of the 132 lakes sampled.  

The Class B(LW) (aquatic life) uses are assessed (monitored) as “fully supported” based on information from the IDNR Fisheries Bureau and results from the ISU and UHL lake surveys.   The ISU and UHL lake surveys show that during 2004-2008 there were no violations of the Class B(LW) criterion for ammonia in 19 samples or dissolved oxygen in 19 samples.   There were 2 violations of the Class A1,B(LW) criterion for pH in 19 samples (11%).   Based on IDNR’s assessment methodology these violations are not significantly greater than 10% of the samples and therefore do not suggest impairment of the Class B(LW) uses at Lake Smith.   Information from the IDNR Fisheries Bureau also suggests that the Class B(LW) aquatic life uses should, due to recent improvements in water quality at this lake, be assessed as "fully supported."  

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

Monitoring and Methods
Assessment Key Dates
7/17/2008 Fixed Monitoring End Date
5/20/2004 Fixed Monitoring Start 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)
Monitoring Levels
Biological 3
Habitat 0
Physical Chemistry 3
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 Primary Contact Recreation Not Impairing
  • Agriculture
  • Internal nutrient cycling (primarily lakes)
  • Natural Sources
  • Not Impairing
  • Not Impairing
  • Not Impairing
Algal Grwth/Chlorophyll a Primary Contact Recreation Moderate
  • Internal nutrient cycling (primarily lakes)
  • Moderate