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<br />.. <br /> <br />Retention_Svstems <br />- werponas <br /> <br />Reftuir~ments <br />Iftunftnance Tconlinued) <br /> <br />1[' <br /> <br />tree growth on the embankment; damage to the emergency spillway; sediment accumulation around the outlet; <br />and erosion within the basin and banks. Any necessary repairs should be made immediately. During inspec- <br />tions, changes to the wet pond or the contributing watershed should be noted, as these may affect basin <br />performance. <br />~. <br />Sediment should be removed from the pond as necessary, ans! at least once eve 5 25 years (usually more <br />frequently than once every 25 years). The frequency of sediment removal depen s on the years of gdiment <br />accumulation that were incorporated into the design volume of the wet pond's permanent pool and forebay and <br />on the OCCUrrence of any high-loading events. <br /> <br />In most cases, no specific limitations have been placed on disposal of sediments removed from wet detention <br />ponds. Studies to date indicate that pond sediments are likely to meet toxicity limits and can be safely <br />landfilled. On-site sediment disposal is always preferable (iflocal authorities permit) as long as the sediments <br />are deposited away from the shoreline to prevent their reenlly into the pond and away from recreation areas, <br />where they could possibly be ingested by young children. <br /> <br />. Sediments should be tested for toxicants in compliance with current disposal requirements if land uses in the <br />catchment include commercial or industrial zones, or ifvisual or olfactory indications of pollution are noticed. <br /> <br />Mosquito control, if necessary. <br /> <br />3-264 <br /> <br />Minnesota Urban Smal~ Sites BMP Manual <br />