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305b Assessments of Stream Conditions in Minnesota's Major River Basins

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305b Assessments of Lake Conditions in Minnesota's Major River Basins

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305b Assessments of Lake Conditions in Minnesota's Major River Basins


Lake assessments are prepared for the U.S. Congress under Section 305b of the Clean Water Act to:

  • estimate the extent to which Minnesota waterbodies meet the goals of the Clean Water Act, and

  • share this information with planners, citizens and other partners in basin planning and watershed management activites.

These assessments are a fundamental part of MPCA's state water quality management program.

Lakes are assessed for the swimmable goal of the Clean Water Act. Categories of assessments for supporting swimming use are:

  • fully supporting (FS)
  • partially supporting (PS)
  • not supporting (NS)

Information about how these assessments are made is available at: Lakes Assessment Process and Methods.

To view assessments of specific lakes, use the Lake Water Quality Assessment Program Data Search.

To view assessments of lakes, select the major river basin from the list of files shown below. Within each major river basin table, lakes are grouped by major watershed. These assessments are based on data collected through 2004.

Basins in Minnesota

basin2n.gif - 18.95 K

PDF Document Minnesota Ecoregions Map


Basin Reports

  • PDF Document 2008 Integrated Report: Surface Water Section (Abbreviated Narrative Report) - Report to the Congress of the United States: Water Years 2004-2005. This report integrates 305b assessments, which measure attainment of standards for fishable and swimmable waters, and 303d (TMDL) listings of impaired waters. Assessments are organized by basin for the entire state and the report also presents statewide summaries. The report describes Minnesota's monitoring and assessment strategy, assessment tools, and the integrated assessment process. It also briefly describes the state's response to these assessments in terms of development and implementaion of TMDLs and special state strategies.

Lake Assessments

Please note that the interative maps below will open in a new browser window. For the interactive maps to work best, your computer should:

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Basin Basin Reports Maps
Cedar and Des Moines River

PDF Document Minnesota Lake Assessments Cedar River - Aquatic Recreation Use
PDF Document Minnesota Lake Assessments Des Moines River - Aquatic Recreation Use

Cedar River Basin for Swimming
Cedar River Basin for Aquatic Consumption

Des Moines River Basin for Swimming
Des Moines River Basin for Aquatic Consumption

Lake Superior PDF Document Minnesota Lake Assessments - Aquatic Recreation Use

Lake Superior River Basin for Swimming
Lake Superior River Basin for Aquatic Consumption

Minnesota River PDF DocumentMinnesota Lake Assessments - Aquatic Recreation Use

Minnesota River Basin for Swimming
Minnesota River Basin for Aquatic Consumption

Missouri River PDF DocumentMinnesota Lake Assessments - Aquatic Recreation Use

Missouri River Basin for Swimming
Missouri River Basin for Aquatic Consumption

Rainy River PDF DocumentMinnesota Lake Assessments - Aquatic Recreation Use

Rainy River Basin for Swimming
Rainy River Basin for Aquatic Consumption

Red River PDF DocumentMinnesota Lake Assessments - Aquatic Recreation Use

Red River Basin for Swimming
Red River Basin for Aquatic Consumption

St. Croix River PDF DocumentMinnesota Lake Assessments - Aquatic Recreation Use

St. Croix River Basin for Swimming
St. Croix River Basin for Aquatic Consumption

Upper Mississippi, Lower Portion PDF DocumentMinnesota Lake Assessments - Aquatic Recreation Use

Upper Mississippi River Basin, Lower Portion for Swimming
Upper Mississippi River Basin, Lower Portion for Aquatic Consumption

Upper Mississippi, Upper Portion PDF DocumentMinnesota Lake Assessments - Aquatic Recreation Use

Upper Mississippi River Basin, Upper Portion for Swimming
Upper Mississippi River Basin, Upper Portion for Aquatic Consumption

Lakes Assessment Process and Methods

Minnesota lake assessments focus on trophic state and its relationship to support of designated uses, specifically swimming and aesthetics. Carlson's Trophic State Index (TSI) was used to combine measures of summer Secchi Disk transparency and epilimnetic concentrations of chlorophyll-a and total phosphorous. The TSI values are calculated as follows:

  • Secchi disk (SD)
    TSI (TSIS) = 60 - [14.41(natural log)(Secchi average)]
  • Total phosphorus (TP)
    TSI (TSIP) = [14.42 (natural log)(TP average)] + 4.15
  • Chlorophyll-a (chl-a)
    TSI (TSIC) = [9.81(natural log)(chl-a average)] + 30.6

(TP and chl-a in micrograms per liter (ug/L) and SD transparency in meters).

The index ranges from 0 to 100 with higher values indicating more eutrophic conditions. The TSI values were calculated for each variable, then averaged for each lake (Figure 1).

Figure 1. Carlson's Trophic State Index (TSI)

TSI <30 Classic Oligotrophy; Clear water, oxygen through the year in the hypolimnion, salmonid fisheries in deep lakes.
TSI 30-40 Deeper lakes still exhibit classical oligotraphy, but some shallower lakes will become anoxic in the hypolimnion during the summer.
TS 40-50 Water moderately clear, but increasing probability of anoxia in hypolimnion during summer.
TS 50-60 Lower boundary of classical eutrophy: Decreased transparency, anoxic hypolimnion during the summer, macrophyte problems evident, warm-water fisheries only.
TSI 60-70 Dominance of blue-green algae, algal scums probable, extensive macrophyte problems.
TSI 70-80 Heavy algal blooms possible throughout the summer, dense macrophyte beds, but extent limited by light penetration. Often would be classified as hypereutrophic.
TSI > 80 Algal scums, summer fish kills, few macrophytes, dominance of rough fish.

Figure 1. Carlson's Trophic State Index

Table 1 provides the Trophic State Thresholds used for determining use support for lakes. Actual detail of the assessment process for 303(d) and 305(b) may be found in the 2004 Minnesota Water Quality Surface Water Section report.

Table 1. Trophic Status Thresholds for Determination of Use Support for Lakes
(Carlson’s TSI noted for each threshold. Taken from guidance manual.)

Table 1. Trophic Status Thresholds for Determination of Use Support for Lakes. (Carlson’s TSI Noted for Each Threshold.). Taken from guidance manual.

Thirtyfour years of data (1970-2004) were used in the assessments. Lakes sampled within the last 10 years are reported as "Monitored", compared with "Evaluated" when assessments are based on monitoring data more than 10 years old. All data are stored in the U.S. Environmental Protection Agency (EPA) "STORET" data system.

Lakes for which no monitoring data were available may have been assessed using a survey of local resource managers, as described below.

Map Shapefiles

The zipped (compressed) file below contains a shapefile which represents the Minnesota 2008 lake assessments (per Section 305(b) Clean Water Act). These files were created for those interested in preparing computerized maps of the 305(b) lake assessments. To use these files you will need Geographic Information System (GIS) computer software. The zipped file contains a shapefile and metadata for aquatic consumption and aquatic recreation use support for lakes. The projection for the shapefile is UTM extended zone 15, NAD83. The shapefile was created by the Minnesota Pollution Control Agency using the 1:24,000 scale National Hydrography Dataset. If you have any questions or comments, please contact Carrie Bartz at 651-757-2214

Zip File Map Shapefile of Minnesota 2008 Lake Assessments (file size = 16 MB)

More Information

For more information about the 305b assessments of lake conditions in Minnesota's major watersheds, contact Steve Heiskary at 651-757-2419. Lower Mississippi River St. Croix River Upper Mississippi River Cedar River Des Moines River Missour River Basin Minnesota River Basin Red River Basin Upper Mississippi River Basin Rainy River Basin