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9.13.23 BOA Agenda Packet
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9.13.23 BOA Agenda Packet
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9/13/2023
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07 June 2023 Page 2 161 <br /> The Nest at 54 West <br /> DEQ Project No.23-0238 <br /> 3. An effective stormwater management plan should be developed for the site. Incorporate the following <br /> elements into erosion and sediment control plans: minimize clearing and grading,protect waterways, <br /> phase construction for larger construction sites(>25 acres), stabilize soils as rapidly as possible(<2 <br /> weeks),protect steep slopes,establish appropriate perimeter controls,employ advanced settling <br /> devices,implement a certified contractors program, and regularly inspect erosion control measures. <br /> 4. Non-native plants should not be used for seeding disturbed areas. Specifically,avoid using <br /> Bermudagrass,redtop,tall fescue,and lespedeza,which are invasive and/or non-native. A list of <br /> alternatives to non-native species has been attached.Alternatively,use a grain, such as oats,wheat, or <br /> rye for temporary cover and native seed mixes for permeant seeding. Avoid using invasive,non- <br /> native plants in seed mixtures or landscaping plants, such as nandina and privet <br /> (hqp://www.ncwildflower.ora/plant_galleries/invasives_list). <br /> 5. Erosion control matting made of plastic mesh or twine should not be used within the project area <br /> because it can injure or kill wildlife. <br /> 6. a)The culvert must be designed to allow for aquatic life and fish passage. Generally,the culvert or <br /> pipe invert should be buried at least 1 foot below the natural streambed(measured from the natural <br /> thalweg depth). If multiple barrels are required,barrels other than the base flow barrel(s)should be <br /> placed on or near stream bankfull or floodplain bench elevation(similar to Lyonsfield design). These <br /> should be reconnected to floodplain benches as appropriate. This may be accomplished by utilizing <br /> sills on the upstream and downstream ends to restrict or divert flow to the base flow barrel(s). Silled <br /> barrels should be filled with sediment so as not to entrap wildlife or support mosquito breeding <br /> conditions. Sufficient water depth should be provided in the base flow barrel(s) during low flows to <br /> accommodate fish movement. If culverts are longer than 40-50 linear feet, alternating or notched <br /> baffles should be installed in a manner that mimics existing stream pattern. This should enhance <br /> aquatic life passage: 1)by depositing sediments in the barrel,2)by maintaining channel depth and <br /> flow regimes, and 3)by providing resting places for fish and other aquatic organisms. In essence, <br /> base flow barrel(s) should provide a continuum of water depth and channel width without substantial <br /> modifications of velocity. <br /> b) If multiple pipes or cells are used,at least one pipe or box should be designed to remain dry during <br /> normal flows to allow for wildlife passage. <br /> c) Culverts or pipes should be situated along the existing channel alignment whenever possible to <br /> avoid channel realignment. Widening the stream channel must be avoided. Stream channel widening <br /> at the inlet or outlet end of structures typically decreases water velocity causing sediment deposition <br /> that requires increased maintenance and disrupts aquatic life passage. <br /> d) Riprap should not be placed in the active thalweg channel or placed in the streambed in a manner <br /> that precludes aquatic life passage. Bioengineering boulders or structures should be professionally <br /> designed, sized, and installed. <br /> Thank you for the opportunity to provide input in the early planning stages for this project. Please contact <br /> me at(336)269-0074 or olivia.munzer(c�r�,ncwildlife.org if there are any questions about these comments <br /> or for free technical guidance. <br />
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