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including soil stockpiles that will be dormant for the area. <br />more than 21 days but less than one year, and not <br />within 50 feet of a stream. <br />Disturbed areas that will be idle over winter. Prior to November 1. <br />Note: Where vegetative stabilization techniques may cause stuctural instability or are otherwise unobtainable, <br />alternative stabilization techni ues must be em to ed. These techni ues may include mulching or erosion mattin . <br />(2) Permanent stabilization of conveyance channels. Applicants shall undertake special <br />measures to stabilize channels and outfalls and prevent erosive flows. Measures may <br />include seeding, dormant seeding, mulching, erosion control matting, sodding, riprap, <br />natural channel design with bioengineering techniques, or rock check dams, all as <br />defined in the most recent edition of Rainwater and Land Development or the Field <br />Office Technical Guide available at www.nres.usda.~ov/technical/efot~/. <br />(c) RUNOFF CONTROL PRACTICES. The SWP3 shall incorporate measures that control the <br />flow of runoff from disturbed areas so as to prevent erosion. Such practices may include rock <br />check dams, pipe slope drains, diversions to direct flow away from exposed soils and <br />protective grading practices. These practices shall divert runoff away from disturbed areas <br />and steep slopes where practicable. <br />(d) SEDIMENT CONTROL PRACTICES. The SWP3 shall include a description of, and <br />detailed drawings for, all structural practices that shall store runoff, allowing sediments to <br />settle and/or divert flows away from exposed soils or otherwise limit runoff from exposed <br />areas. Structural practices shall be used to control erosion and trap sediment from a site <br />remaining disturbed for more than 14 days. Such practices may include, among others: <br />sediment settling ponds, silt fences, storm drain inlet protection, and earth diversion dikes or <br />channels which direct runoff to a sediment settling pond. All sediment control practices must <br />be capable of ponding runoff in order to be considered functional. Earth diversion dikes or <br />channels alone are not considered a sediment control practice unless used in conjunction with <br />a sediment settling pond. <br />Sediment control practices must meet the following requirements: <br />(1) Timing. Sediment control structures shall be functional throughout the course of <br />earth disturbing activity. Sediment basins and perimeter sediment barriers shall be <br />implemented prior to grading and within seven (7) days from the start of grubbing. <br />They shall continue to function until the up slope development area is restabilized. <br />As construction progresses and the topography is altered, appropriate controls must <br />be constructed or existing controls altered to address the changing drainage patterns. <br />(2) Sediment settlingponds. Concentrated storm water runoff and runoff from drainage <br />areas that exceed the design capacity of silt fence or inlet protection, as determined in <br />Table 3 below, shall pass through a sediment settling pond or equivalent best <br />management practice upon approval from the Mayfield Village Engineer. <br />The sediment-settling pond shall be sized to provide at least 67 cubic yards of storage <br />per acre of total contributing drainage area. When determining the total contributing <br />drainage area, off-site areas and areas which remain undisturbed by construction <br />activity must be included unless runoff from these areas is diverted away from the <br />sediment settling pond and isnot co-mingled with sediment-laden runoff. The depth <br />of the sediment-settling pond must be less than or equal to five (5) feet. The <br />