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<br />. <br /> <br />Retention_Svstems <br />- "W'erponc1s <br /> <br />percent (SEWRPC, 1991). Seepage through the embankment can also affect the stability of the structure. Seep- <br />age can generally be minimized by adding drains, anti seepage collars, and core trenches. The embankment side <br />slopes can be protected from erosion by using minimum side slopes of3:] and by covering the embankment with <br />vegetation or riprap. The embankment should also have a minimum top width of2 meters (6 feet) to aid in mainte- <br />nance. <br /> <br />Scour Control: <br /> <br />Scour is the erosion of pond bottom or bank material due to high flow velocities. Scour control is important to <br />maintain the function of the pond and reduce erosion, especially near the inlet. Inlet areas and inlet structures <br />should be designed to control velocities at the inlet whether from large or small storm events. <br /> <br />Flow-diffusion devices, including plunge pools, directional berms or other specially created dissipation structures, <br />are often recommended. For annual events, the velocity leaving the inlet area and entering the main treatment area <br />should be less than I foot per second (fps). Decreasing velocity reduces scour and more importantly reduces <br />mixing currents that reduce treatment efficiency. <br /> <br />The MPCA recommends that the following design storms be considered in the pond design (MPCA, 2000). Scour <br />prevention can be achieved if velocities through the main treatment area are limited to the following maximums: <br /> <br />I foot per second for the I-yr 2.4" event: <br /> <br />3 feet per second for the 2-yr, 2.8" event: <br /> <br />5 feet per second for the 10-yr, 4.0" event and the 100-yr, 6.0" event <br /> <br />Velocities are calculated as outflow divided by the area of the critical cross-section. All events are considered to <br />be the 24-hour NRCS distribution event. . <br /> <br />Water Quantity Control Requirements: <br /> <br />Wet ponds should be designed to meet both storm water quality and quantity control requirements. Storm water <br />quantity requirements are typically met by designing the pond to control post-development peak discharge rates to <br />pre-development levels. Usually the pond is designed to control multiple design storms (e.g. 2- and/or 10-year <br />storms) and safely pass the 100-year storm event. However, the design storm may vary depending on local <br />conditions and requirements. <br /> <br />Design for Winter-Runoff Conditions <br /> <br />During the winter period, the design volume of the wet pond can be less than desired. Ground freezing throughout <br />the tributary watershed effectively increases the watershed's imperviousness, which increases the fraction of <br />precipitation that reaches the pond. Moreover, the available volume in the permanent pool can be reduced by the <br />formation of ice. Fortunately, winter rainfall and snowmelt events (as opposed to spring) typically produce lower <br />volumes of runoff than summer storms and so most events will continue to be captured entirely (e.g, the volume of <br />runoff will be less than the reduced volume of the wet pond). However, temperature regimes in the northern <br />regions of Minnesota are such that ice cover may persist into the spring period when runoff rates and contaminant <br />washoff rates are higher. In these areas, some authorities recommend that the wet pond volume be increased by <br />an amount equal to the expected volume ofthe ice cover (Ontario Ministry of the Environment, 1999). <br /> <br />Metropolitan Council! Barr Engineering Co. <br /> <br />3-261 <br />