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Stormwater Policy
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Stormwater Policy
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7/9/2014 4:51:26 PM
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03/07/9b v:4& QJUJ LL4 IGLU <br /> • <br /> invert to allow sediment and debris accumulation and removal and a baffle at <br /> the outlet to prevent floating materials from entering the storm drain pipe. <br /> • Sedimentation manholes — simple variations on the traditional manhole and <br /> placed upstream from infiltration sumps and other water quality facilities. <br /> Similar to trapped catch basins, the majority of the manhole is located below <br /> the pipe invert to allow sediment and debris accumulation and removal. <br /> • Underground detention vaults /tanks —large underground detention facilities <br /> that store runoff. Wet tanks and vaults maintain a permanent pool of water to <br /> provide quiescent settling conditions so particulates (and attached pollutants) <br /> will settle and collect at the bottom. These facilities are usually constructed <br /> from reinforced concrete (vaults) or corrugated metal pipe (tanks). <br /> Prior to recommending guidance references for these facilities, it is important to <br /> inform staff about the current school of thought related to performance. <br /> These devices involve limited, if any, biological processes and rely on gravity settling <br /> to reduce sediment loads in stonnwater runoff. Sedimentation allows insoluble <br /> particulates and their attached pollutants to separate from the runoff. Structural <br /> devices in this category have been declining in popularity for use as stormwater quality <br /> devices as more information is learned about actual pollutant removal efficiencies and <br /> performance. Some agencies are recommending that designers consider other options <br /> such as filters and infiltration, before selecting structural control devices. <br /> Eugene will need to make a decision about applicability of the structural devices <br /> outlined above to the local conditions, in light of recent findings in other locales. <br /> Oil/water separators have proven applications in treating industrial process waters <br /> (provided they are properly maintained); however, their track record at stormwater <br /> runoff pollutant removal has been generally poor due to the highly variable flow with <br /> high discharge rates, turbulent flow regimes, and high suspended solids content of <br /> typical urban runoff. Sedimentation manholes continue to be used in the Portland <br /> area with little known about their actual effectiveness. A study conducted by the City <br /> in 1994 found that removals of phosphorus and total suspended solids were not <br /> significant. Similarly, no studies have been performed to test the effectiveness of <br /> vaults/tanks, although, in theory, one should be able to design the volume of these <br /> devices to achieve reasonable pollutant removals through settling. <br /> In general, the effectiveness of all the devices discussed in this chapter depends on <br /> routine maintenance. Without maintenance, devices that accumulate large volumes of <br /> sediment and oil will clog or release those pollutants during high flows. For this <br /> reason it is now commonly recommended that some of these devices, such as oil /water <br /> separators, be constructed off -line, thereby allowing high flows to be bypassed. Also, <br /> S \945042na \task0200 \onsite conrrols\techmem.ck 13 <br />
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