Through the Mustinka River Watershed Restoration and Protection Strategy high priority locations have been identified as critical areas to reduce sediment from agricultural fields. The goal of this project is to target one of the areas that is of high concern, the watershed of Traverse County Ditch 37. This effort intends to begin a program to install side inlets and erosion control berms along the ditch with the goal of reducing the sediment load by 340 tons of sediment per year.
This project will provide support for the 10th Annual Road Salt Symposium at the Minnesota Landscape Arboretum. The symposium brings together environmental organizations, companies that produce winter road de-icing salts and chemicals, scientists, policy-makers and transportation workers. They Symposium provides information on chlorides in our waters and provides innovative and new approaches to help repair our waters and sustain our resources for future generations.
The goal of this project is to continue and finalize Hydrologic Simulation Program FORTRAN (HSPF) watershed model construction and complete the calibration/validation process. The project will add representation of point source discharges to the model, compile flow and water quality data for the purposes of calibration and validation. The end result will be an HSPF watershed model that can readily be used to provide information to support conventional parameter TMDLs.
The goal of the project is the development of an overall strategy for reduction of turbidity/TSS, with sets of sediment reduction initiatives and actions for various sources, to address the Minnesota River Turbidity TMDL and the South Metro Mississippi River TSS TMDL.
The Wright SWCD applied for, and received, a Soil Erosion and Drainage Law Compliance grant in 2015. This grant was used to inventory Joint Ditch 15 (JD 15) for areas that could benefit from the installation of Side Inlet Control Structures (SICS) and vegetated buffer strips (buffers). JD 15 is known to have areas of significant erosion that effect both benefited landowners as well as a number of impaired waters downstream. The impaired downstream waters include Sucker Creek, Cokato Lake, and the North Fork Crow River. The JD 15 Inventory was completed during the summer of 2015.
MSU-Mankato Water Resources Center in the Mankato area will provide conventional pollutant monitoring at the following sites: Beauford Ditch, Big Cobb River, Blue Earth River, Le Sueur River (3), Little Cobb River, Minnesota River (2), Watonwan River.
The overall goal of this project is to perform water quality monitoring duties to accomplish MPCA’s SWAG monitoring efforts at the four sites listed in Section IV of this application for the Middle Minnesota River stream sites selected in Renville, Redwood and Brown counties and allow for the assessment of aquatic life and aquatic recreation use for those reaches of the minor streams.
The goal of this project is to establish data sets to evaluate the Aquatic Recreational Use of Mallard, Sucker, and Ozawindib Lakes in southeastern Clearwater County.
The goal of this project is to assess water quality in the following Anoka County waterbodies: Minard Lake, Pickerel Lake, Trott Brook, Seelye Brook, Cedar Creek, and the Rum River.
The goal of this project is to complete a two-year data set for physical, bacterial, and water chemistry sampling for the Intensive Watershed Monitoring Plan to aid MPCA’s assessment of the aquatic health of the Mississippi Headwaters(HUC 07010101) Watershed.
The primary goal of this project is to accurately collect surface water quality data to help support the MPCA’s Intensive Watershed Monitoring efforts in the Lake Superior North Watershed.
The goal of this project is to collect data, water chemistry and field parameters, which will be paired with biological data collected by the MPCA to assess water quality conditions at seven sites along targeted reaches within the Snake River Watershed and five sites in the Two River Watershed.
The goal of the project is to complete the dataset for the assessment of Aquatic Recreation Use in Cedar Lake by monitoring total phosphorus, chlorophyll-a, and secchi depth.
This project will support the monitoring of two sites on the Cannon River throughout the field seasons of 2013 and 2014 during storm events and baseflow conditions to capture 25 samples per year at each site according to the WPLMN objectives. The information gathered from these samples and site visits will be compiled for reporting purposes and for use in calculating pollutant loading using the FLUX32 model.
This project will monitor six sites within the Minnesota River Basin: Hawk Creek near Maynard, Hawk Creek near Granite Falls, Beaver Creek near Beaver Falls, Yellow Medicine River near Granite Falls, Yellow Medicine River near Hanley Falls, and Spring Creek near Hanley Falls. The sites will be monitored according to MPCA’s Major Watershed Load Monitoring (WPLMN) Standard Operating Procedure, which is the procedure being followed for sites currently monitored by the Hawk Creek Watershed Project (HCWP).
The MPCA has identified 13 stream sites in the watershed to characterize watershed water quality. This project will supplement and complement the identification of the top 50 sites in the watershed that are contributing to water impairment and also help in identification of priority watersheds in the re-write of the watershed comprehensive plan. Water samples and field measurements will be collected at each monitoring location ranging from baseline events to high flow events.
This project will obtain spatial and long-term pollutant load information from the Root River watershed in Southeast Minnesota. To accomplish this, the Fillmore Soil and Water Conservation District (SWCD) will assist the MPCA with water quality monitoring and annual pollutant loading calculations. Approximately 25 grab samples will be collected/site/year at 5 sites within the Root River watershed (totaling 125 grab samples/year). Annual load calculations for each site will be determined using the FLUX32 model.
This project will work with the MPCA to conduct watershed pollutant load monitoring at four sites in the Chippewa River watershed and one site in the neighboring Pomme de Terre River watershed . The Chippewa River Watershed Project (CRWP) team will also aid the MPCA in measuring and comparing regional differences and long-term trends in water quality. The goal is to collect quality data and complete load calculations for the five sites using the MPCA's established protocols.
The goal of this project is to perform water quality monitoring and load calculation duties to accomplish MPCA's Watershed Pollutant Load Monitoring Network monitoring efforts at seven sites for the Redwood and Cottonwood River watersheds as well as the Minnesota River site near Morton.
This project goal is to conduct water chemistry monitoring at seventeen stream locations, to record and submit all data collected through this process, and to provide the information necessary for the calculation of water quality pollutant loads using the FLUX32 program.
This project targets retrofit stormwater Best Management Practices (BMPs) on public land to assist partnering Local Government Units (LGUs) achieve water quality goals identified in local stormwater plans. The Dakota County Soil and Water Conservation District (SWCD) provides technical assistance and distributes Clean Water Funding (CWF) to leverage local funding through its time-proven Stormwater Retrofit Partnership (Partnership) cost share program.
This project is a continuation of the Dakota County Community Initiative, which has received Clean Water Funds in 2012 and 2013. It will provide cost share funding to organizations and associations who voluntarily construct medium sized water quality best management practices (BMPs) in Dakota County.
The Red River is impaired for sediment. This project will install best management practices to repair severe gullies that are contributing massive sediment loads to the Red River. The City of Moorhead also draws water from the Red River for its drinking water supply downstream. The proposed practices will reduce water treatment costs upon installation. Grant funds will be used to install four grade stabilization structures. These structures will control concentrated runoff and reduce flow velocities.
The Winona County Soil and Water Conservation District (SWCD) developed this project to help reduce the amount of pathogens and nutrients generated by livestock from reaching surface waters and groundwater by targeting feedlots located in areas that are highly susceptible to groundwater pollution and sinkhole formation.
The City of Thief River Falls drinking water is taken from a 135 acre reservoir that is supplied by the Thief River and Red Lake River. Sedimentation and erosion have significant impacts to the waters in Pennington County. The reservoir is filling with sediment faster than expected. Buffers and side water inlets will help reduce sediment and improve water quality for these types of erosion. Buffers would also reduce nutrients polluting the waters in Pennington County and have a beneficial impact to the dissolved oxygen impairment on both the Red Lake and Thief River.
Wabasha Soil and Water Conservation District, in conjunction with Wabasha Natural Resources Conservation Service field office and Farm Service Agency field office, will complete 75 compliance checks and writing or rewriting Highly Erodable Lands plans throughout Wabasha county. Technical staff, upon completion, will partner with landowners to coordinate potential future funding to increase conservation on the land and increase water quality in streams and groundwater through Best Management Practices placement.
Lower Prior Lake was the target of a 2011-2013 diagnostic and feasibility study that identified projects and ranked subwatershed by phosphorus loading to the lake. This project is in a high loading subwatershed and includes three elements designed to reduce phosphorus loading and control rates and volumes of stormwater runoff: 1) retrofitting an existing ditch section with in-line iron-sand filters; 2) expanding storage capacity and creating wetland upstream of the ditch; and 3) installing a new control structure in an existing berm.
Arctic Lake, while not listed as an impaired water on the statewide 303(d) list, both regularly exceeds the statewide phosphorus standard for shallow lakes and drains directly to Upper Prior Lake, which is impaired for nutrients Reducing Phosphorus to Arctic Lake will help reverse the current declining water quality while also reducing the loading entering Upper Prior Lake.
