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305b Assessments of Stream Conditions in Minnesota's Major River Basins Related Pages: 305b Assessments of Lake Conditions in Minnesota's Major River Basins This Web site contains PDF documents that require Adobe Acrobat for viewing. |
305b Assessments of Lake Conditions in Minnesota's Major River BasinsLake assessments are prepared for the U.S. Congress under Section 305b of the Clean Water Act to:
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:
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
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| 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. |
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.)
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.
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
Map Shapefile of Minnesota 2008 Lake Assessments (file size = 16 MB)
For more information about the 305b assessments of lake conditions in Minnesota's major watersheds, contact Steve Heiskary at 651-757-2419.
This page was last updated December 19, 2008
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