» \ HI O Section 319 NONPOINT SOURCE PROGRAM SOCGESS STORY Managing Agricultural Drainage Reduces Bacteria in Clearwater River Waterbodv Improved NonP°int sources °f pollution, such as livestock operations, wildlife, and drainage from wild rice paddies, contributed high levels of bacteria in Minnesota's Clearwater River that violated water quality standards. As a result, the Minnesota Pollution Control Agency (MPCA) added a 58-mile segment of the Clearwater River to the state's Clean Water Act (CWA) section 303(d) list of impaired waters in 2002 for pathogens impairment. Project partners implemented a number of restoration projects, including planting buffer strips, stabilizing streambanks and improving the drainage of wild rice paddies. These efforts have reduced bacteria levels; as a result, MPCA removed the 58-mile segment of Clearwater River from the state's 2010 list of impaired waters for bacteria. Problem The 886,600-acre Clearwater River watershed (Figure 1) drains portion of Clearwater, Mahnomen, Polk and Red Lake counties in northern Minnesota's Red River Basin. Major land uses in the watershed include agriculture (54 percent), forest (24 percent) and wetlands (14 percent). The watershed has a poorly defined floodplain and low gradient, and it has been altered by extensive drainage, wide- spread conversion of tallgrass prairie to farmland, and urban/suburban development. As a result, the basin is subject to frequent floods that affect urban and rural infrastructure, as well as agricultural production. Between 1948 and 1958, the U.S. Army Corps of Engineers channelized approximately 38 miles of the Clearwater River to reduce flood damage to agricultural interests in the surrounding area. This channelization has exacerbated upstream streambank erosion problems, leading to increased sediment loading in the river. The "Clearwater River Nonpoint Study," completed in the early 1990s, found that the monthly geo- metric mean fecal coliform bacteria concentra- tions exceeded the state's water quality standard in June, August and September. As a result, the MPCA added a 58-mile segment of Clearwater River (from its confluence with Ruffy Brook to its confluence with the Lost River) to Minnesota's CWA section 303(d) list of impaired waters in 2002; the reason given was failure to meet the state's bacteria water quality standards to protect the waterbody's aquatic recreation designated use. Red Lake Red Lake Minnesota Figure 1. Northwestern Minnesota's Clearwater River is in the Red Lake River basin, a tributary of the Red River of the North. Nonpoint sources of fecal coliform included live- stock operations, wildlife, and drainage from wild rice paddies along the river. Hydrologic modifica- tion also contributed to pollution problems. This segment was also listed in 2002 as impaired for dissolved oxygen. ------- Figure 2. Farmers restored streambanks and installed vegetated buffer strips along the river. Project Highlights Numerous studies and implementation activities led to the improved water quality of Clearwater River. The Clearwater County and Red Lake County soil and water conservation districts worked with farmers to implement best management practices (BMPs) throughout the watershed. The BMPs included residue management, grazing management, nutri- ent management, grade control structures, side water inlets, streambank protection and grassed waterways. The soil and water conservation districts worked with local farmers with lands adjacent to the river to install vegetated buffer strips along the river to minimize erosion and intercept and filter runoff (Figure 2). Farmers also modified stretches of ditches to function as sediment traps. In 2001, farmers used CWA section 319 grant funds to install erosion con- trol and streambank stabilization BMPs at key sites in the watershed. A number of wild rice growers along the Clearwater River installed tile drainage in their paddies, which reduced the amount of sediment and waterfowl manure leaving the paddies. Results The Red Lake Watershed District, with support from the MPCA, conducted a total maximum daily load (TMDL) study from 2007 to 2009 to assess impair- ments, define sources and loads of pollutants, esti- mate the reductions in pollutants needed to meet water quality standards, and propose strategies to achieve the desired reductions. During the course of the TMDL study, Minnesota's aquatic recreation water quality standard transitioned from a fecal coliform bacteria-based standard to an Escherichia co/i bacteria standard of a maximum monthly mean of 126 colony-forming units (CFU) per 100 mL. Throughout the two-year study, at least five water samples were collected monthly from several locations along the Clearwater River. All samples collected within the two-year monitoring period met the state's £ co/i water quality standard to protect the waterbody's aquatic recreation designated use (Figure 3). Based on these results, the MPCA confirmed that the Clearwater River segment no longer required a TMDL to address the bacteria impairment and removed the 58-mile segment from the state's list of impaired waters in 2010 for bacteria. Stakeholders continue to set pollution reduction goals to further improve water quality and are developing a Clearwater River Protection Plan to coordinate these efforts. The segment remains listed as impaired for dissolved oxygen. Clearwater River at Plummer USGS Gauge (Site 780) January February March" April May; June July" August" September October" November • 1 sample ^^™ 1 sample ^•18 samples mples s lies nn l 4 samples es 0 25 50 75 100 125 Monthly Geometric Mean £ Co// Concentration, Most Probable Number* (MPN)/100 ml *MPN and CFU are essentially equivalent for comparison purposes. Figure 3. Clearwater River monthly geometric mean E. co/i data (2007-2009). Partners and Funding The success of the Clearwater River Nonpoint Project was the result of coordination between local, state and federal agencies. The Phase I (study) portion of the project was completed by the Red Lake Watershed District (RLWD) and HDR Engineering and was sponsored by the RLWD and local soil and water conservation districts. Phase II of the project (implementation) was also admin- istered and implemented by the RLWD. In 2001, a $134,500 CWA section 319 grant funded stream bank stabilization projects in the watershed. CWA section 319 funds also supported the MPCA staff who served in an advisory role throughout the life of this project. State funding provided additional sup- port, including an $852,541 loan from Minnesota's Clean Water Partnership in 1996 and 2001, and a grant of $100,000 from the 2007 Clean Water Legacy state appropriation. s » U.S. Environmental Protection Agency Office of Water Washington, DC EPA841-F-12-001K May 2012 For additional information contact: Corey Hanson, Red Lake Watershed District 218-681-5800 • coreyh@wiktel.com Jim Courneya, Minnesota Pollution Control Agency 218-846-8105 • Jim.courneya@pca.state.mn.us ------- |