"%
                 NONPOINT SOIRCf SICCESS STOIY
  Coordinated Efforts Reduce Polluted Stormwater Runoff, Improving
  Water Quality in Lower Twin and Ryan Lakes
Waterbodies Improved
                                    Nutrients in stormwater runoff led to eutrophic conditions
                                    in Lower Twin Lake and Ryan Lake in the Minneapolis
metropolitan area. Because of these conditions, Minnesota added both lakes to its 2002 Clean
Water Act (CWA) section 303(d) list of impaired waters for failing to attain their aquatic  recreation
designated uses. Implementing best management practices (BMPs) throughout the watershed
decreased nutrient runoff and improved water quality in the lakes, allowing Minnesota to remove
them from its impaired waters list in 2014.
 Problem
  Lower Twin Lake and Ryan Lake are in the Shingle
  Creek watershed in the northwestern Twin Cities
  metropolitan area in Minnesota (Figure 1). The lakes
  are part of the Twin Lake chain of lakes, which includes
  Upper Twin, Middle Twin, Lower Twin and Ryan
  lakes. The chain of lakes flows into Shingle Creek and
  ultimately the Mississippi River. The Shingle Creek
  Watershed Management Commission (SCWMC) is the
  local entity responsible for protecting the watershed's
  lakes, streams and wetlands.

  The SCWMC contains nine cities, 16 lakes, seven
  streams and numerous wetlands. The majority of the
  Shingle Creek watershed is developed, with industrial,
  commercial and residential land uses present. The
  Lower Twin and Ryan lake subwatersheds are fully
  developed with single and multi-family residential land
  uses. Together, the lakes drain more than 8 square miles
  of land. The lakes are regularly used for recreational
  activities such as canoeing and fishing.

  Minnesota water quality standards for aquatic life and
  recreation for shallow lakes in the summertime (June-
  September) require that (1) the average total phospho-
  rus (TP) concentrations are equal to or less than (<)
  60 micrograms per liter (u.g/L), (2) chlorophyll-o (chl-o)
  concentrations are < 20 u.g/L, and (3) Secchi disc (SD)
  transparency is at least 1.0 meter (3.3 feet). For deep
  lakes, the standards are more stringent, requiring
  that the summertime average TP concentrations are
  < 40 u.g/L, chl-o concentration are < 14 u.g/L, and SD
  transparency is at least 1.4 meters (4.6 feet).
                                                 B
L
Lower Twin and Ryan Lakes
Shingle Creek Watershed
 Data sources include *305(b) assessed lakes s
                                      1 Miles
                                                                           He, Watershedboundaiy •
                                                "^ - I  dataset, US. Census Bureau state map, and USGS Topo Basemap.
                                                Figure 1. Lower Twin and Ryan lakes are in the Shingle
                                                Creek watershed in eastern Minnesota.

                                                Historical water quality trends indicated that the
                                                lakes exceeded Minnesota Pollution Control Agency's
                                                (MPCA's) water quality standards until the 2000s for
                                                shallow lakes (i.e., Lower Twin Lake) and deep lakes
                                                (i.e., Ryan Lake). On the basis of these data, MPCA
                                                added the two lakes to the state's 2002 CWA section
                                                303(d) list of impaired waters for excess nutrients/
                                                eutrophication. In 2007 MPCA finalized a  phosphorus

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120

100
      Lower Twin Lake Water Quality (2000-2012)
                                           •1
                                           ,1
                                   O  t—  r*j
        • Total Phosphorus
I Chlorophyll-a
                                         I Secchi Depth
       Figure 2. Data show that Lower Twin Lake has met all three
       shallow-lake water quality standards since 2010.

          total maximum daily load (TMDL) for the lakes and
          developed a TMDL implementation plan. The TMDLs
          indicated that to attain standards, phosphorus loads
          must be reduced by zero to 65 percent in Lower Twin
          Lake and by zero to 54 percent in Ryan Lake.
Project Highlights
Watershed stakeholders have cooperated on numer-
ous projects to reduce nutrients in runoff. In the
Lower Twin Lake watershed, the city of Robbinsdale
increased street sweeping to four times per year and
installed several rain gardens, stormwater ponds and
grit chambers beginning in 2004. Also since 2004,
Hennepin County and the Minnesota Department of
Transportation installed numerous BMPs as part of
highway reconstruction projects. In 2011 the city of
New Hope expanded a stormwater pond to maximize
the removal of sediment and phosphorus from runoff.

Similar efforts have occurred in the  Ryan Lake
watershed. Since 2004, the city of Brooklyn Center
has installed five sump manholes that remove sus-
pended sediment from runoff. In 2004 the Victory
Neighborhood Association planted more than
6,000 native plants on an eroding shoreline, and then
partnered with the city of Minneapolis in 2013 to
install 15 rain gardens.

Both lakes have benefited from the ongoing efforts
(since 2004) of the SCWMC and local partners to reduce
phosphorus and improve water quality in upstream
impaired lakes. In 2013 the SCWMC updated the Shingle
Creek Watershed Management Plan  and development
rules to require higher stormwater infiltration capacity.
                                             Ryan Lake Water Quality (2000-2012)
                                                                    140

                                                                    120

                                                                    100

                                                                    80

                                                                    60

                                                                    40

                                                                    20

                                                                                '1
                                                                         388
                                                                • Total Phosphorus
                                                                                      88888
                                                                             I Chlorophyll-a   • Secchi Depth
                                                      Figure 3. Data show that Ryan Lake has met all three deep-
                                                      lake water quality standards since 2008.
                                                     Results
                                 Recent monitoring data indicate that water quality
                                 has improved in both lakes: TP and Chl-o concentra-
                                 tions have decreased, while SD transparencies (mean
                                 June-September) have increased. Lower Twin Lake has
                                 consistently met shallow-lake water quality standards
                                 since 2010 (Figure 2). Ryan Lake has met deep-lake
                                 water quality standards since 2008 (Figure 3). As a
                                 result of these improvements, MPCA removed Lower
                                 Twin Lake (MN27-0042-03; 30 acres) and Ryan Lake
                                 (MN27-0058-00; 15 acres) from the list of impaired
                                 waters in 2014.
                                 Partners and Funding
                                 The restoration of Lower Twin and Ryan lakes was
                                 supported by many partners and funding sources.
                                 Specific partners included SCWMC, the Minnesota
                                 Board of Water and Soil  Resources, the National Park
                                 Service, Minnesota  Department of Transportation,
                                 Minneapolis' Victory Neighborhood Association, the
                                 nonprofit Metro Blooms, Hennepin County, and the
                                 cities of New Hope,  Minneapolis, Robbinsdale and
                                 Brooklyn Center.

                                 Project funding included $6,200 in Hennepin County
                                 Natural Resources Incentives for Critical Habitat funds,
                                 $52,908 in SCWMC  Capital Improvement Program
                                 funds, $160,000 in Clean Water Legacy Grant funds,
                                 $1,762 in funds from the city of New Hope, and $3,600
                                 in National Park Service Challenge Cost Share funds.
                                 SCWMC served as the lead on these projects and the
                                 project manager was funded using CWA section 319
                                 match funds.
I
9
        U.S. Environmental Protection Agency
        Office of Water
        Washington, DC


        EPA841-F-16-001E
        February 2016
                                 For additional information contact:
                                 Judie Anderson
                                 Administrator, SCWMC
                                 judie@jass.biz • 763-553-1144
                                 Rachel Olmanson
                                 Watershed Project Manager, MPCA
                                 rachel.olmanson@state.mn.us • 651-757-2473

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