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05/26/2009 13:27 9518273349 DOUGLAS KUNEY PAGE 09/14 <br /> promaie dissolution of gases, minimize escape of odors, and <br /> require less land area for a given treatment volume. <br /> Lagoon shape can affect the mixing of its �ontents, <br /> Circular and square sbapea usually promotalbest mixing, but <br /> elliptical and rectangular lagoons may be used if their <br /> lwtgth to width ratio dors not exceed as1. The periphery <br /> should be uniform and free of pockets, isldnds,, and coves <br /> which contribute little additional grater v6lume to 'the <br /> lagoon, and may be a source of nuisance conditions. special <br /> cases may justify long narrow lagoons, espici.ally for flow- <br /> through units in multiple-stage systems, and where <br /> construction and de�-sludginq will be accom-Alish&d by <br /> dragline. Lagoon bottoms should be as fla as possible to <br /> promote uniform 4istri]2ution of wastes. <br /> Side slopea are primarily determined by soil type, with more <br /> stable soils adaptable to steeper slopes. Steep slopes <br /> below the waterline discourage weed growth 1 and mosquito <br /> habitat. Flatten slopes, normally 3:1, sh d be used above <br /> the maximum waterline to allow easy establisbment of ground <br /> cover and safer mowing. bake the top of ail embankments at <br /> least 8 feet oxide for equipment travel andioperation. <br /> Emban]aatent height should be increased durir1q construction by <br /> the amount noeded to enm=e that design top elevation will <br /> be achieved after settlemeatf minfwum increase should <br /> norAkUly be 5 pelt. <br /> Locate inlets near the center of the lagoo� if possible to <br /> a o:zrage <br /> solids distribution throughout tfie impoundment <br /> Multiple housing units usually permit use cif several inlets <br /> to further aid in uniform distribution. Zia of gutter <br /> cleansers or augers to move manure directlyiinto the lagoon <br /> may result in large deposits of manure at i is loading point, <br /> but it the drop point is beyond the embank int slope and' <br /> loading points are well di,stri.buted, bacteiial activity and <br /> gas bubbling will eventually distribute wanes through the <br /> lagoon. <br /> Additional lagoon doptk above u4nimum treatment design depth <br /> (Figure 1) should be provided for waste steerage between <br /> projected pumpdown events. The exact amount of storage <br /> planned will be dependent upon the managplan. At <br /> least 90 days of storage should be providea in mild <br /> alin&teas more st=age will be required iz II colder climates <br /> to avoid applying treated effluent on from ground <br /> Cr ing patterns should also be considered so that effluent <br /> may be hold until it Mm be effectively utilized as a crop <br /> nutrient source. Additional depth should be provided to <br /> allow for precipitation from a 35-year, 24�bour stare <br /> falling on the lagoon surface and embartkme is when the <br /> lagoon is at the full level, lura capacity must also be <br /> planned if other surface runoff will enVwl the lagoon. An <br /> additional i ft, of freeboard Avertical dice between <br /> 272 <br /> y <br />