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Pearson Farm Residential Development EAW Draft — March XX, 2017 <br />one- and two-year storms. Section 117-394 of the City Code protects natural wetlands from the <br />discharge of stormwater without appropriate treatment for water quality and runoff quantity control. <br />The minimum treatment required for discharge to wetlands is to meet NURP Guidelines, which <br />include a dead storage treatment pond volume at least equal to the runoff from a 2.5 inch storm over <br />the entire contributing area assuming full development, an average pool depth of more than 3, and a <br />maximum depth of 10 feet. LRRWMO Stormwater Standards require stormwater basins designed to <br />store the volume of the 100-year storm; stormwater treatment to NURP standards prior to discharge <br />to a lake, stream, wetland, or offsite; and infiltration of a runoff volume equal to 1 inch from all <br />impervious surfaces onsite. <br />Potential adverse effects of runoff volume and quality will be mitigated by the construction of <br />stormwater basins designed to manage peak runoff rates, runoff volume, and water quality. <br />Impervious surface runoff from storm events will be retained in four stormwater ponds and one or <br />two infiltration basins until it is discharged at or below existing peak runoff rates. Wetlands on the <br />site provide potential for additional runoff storage and infiltration. Treated stormwater runoff from <br />the site will be routed east under Puma Street NW into an existing intermittent drainageway, and <br />eventually into the City's storm sewer system that ultimately reaches the Mississippi River. <br />Proposed discharge flow rates will be equal to or less than the existing flow rates. <br />Stormwater ponds designed to NURP criteria are considered effective in removing sediment, <br />pollutants, and nutrients, as discussed in Protecting Water Quality in Urban Areas: Best Management <br />Practices for Dealing with Storm Water Runoff from Urban, Suburban and Developing Areas of <br />Minnesota (MPCA 2000). The NURP research projects conducted by the U.S. EPA concluded that <br />90% removal of total suspended solids was an attainable goal, and that significant removal of other <br />pollutants, such as phosphorus, was also achievable. Although nutrient removal efficiency varies <br />with site conditions, well -designed wet ponds and constructed wetland treatment systems are <br />effective in removing sediment and associated pollutants, such as trace metals, nutrients and <br />hydrocarbons. Stormwater basins also remove or treat oxygen -demanding substances, bacteria and <br />dissolved nutrients. <br />Other BMPs such as vegetative buffer strips are expected to filter sediment and nutrients from runoff <br />before it reaches wetlands and surface waters, mitigating potential effects on water quality. <br />LRRWMO Wetland Protection Standards require establishment of native vegetation within a 16.5- <br />foot-wide buffer strip around wetland boundaries. Temporary sediment basins will be necessary to <br />comply with the MPCA General Stormwater Permit for Construction Activity and to manage <br />stormwater discharge during construction. <br />Stormwater and Erosion Control BMPs <br />Because project construction will involve disturbance of more than one acre of land, the project <br />proponent will be required to apply to the MPCA for coverage under the National Pollutant <br />Discharge Elimination System/State Disposal System (NPDES/SDS) General Permit prior to <br />initiating earthwork on the site. BMPs will be employed during construction to reduce erosion and <br />sediment loading of stormwater runoff. Inspection of BMPs will be required after each rainfall <br />exceeding 0.5 inches in 24 hours, and on a routine basis every 7 days. The NPDES permit will also <br />14 <br />