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Advances in Water Treatment and Enviromental Management

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228 WATER TREATMENTstreams of low water content, with m<strong>in</strong>imal rates <strong>in</strong> the warm seasons up to 30m3/s, low rates of flow, below 0.3 m/s, <strong>and</strong> specific river discharge per one urban<strong>in</strong>habitant below 0.03 l/s. Urban reservoirs with low fiowage, with specific watervolume less than 1000m 3 per 1 ha of built-up adjo<strong>in</strong>ed territories, can also be<strong>in</strong>cluded <strong>in</strong> this category.Traditionally SS loads can be reduced by construction of a partially separate systemwith partial bypass to the municipal sewage treatment works, or sedimentationlagoons at swere outfalls, <strong>and</strong> <strong>in</strong> exceptional cases filters can be provided for tertiarytreatment.<strong>Treatment</strong> of NP discharge gives relatively small BOD reduction, only about 3–6 %of the raw municipal sewage BOD, but capital <strong>in</strong>vestments for this purpose arecomparable with that for municipal sewage treatment works. Capital <strong>in</strong>vestmentseven for simplest NP discharge treatment, such as lagoons, when calculated perone tone of captured organics, are 2–3 times higher than for tertiary treatment ofmunicipal sewage.Such high specific costs, especially capital ones, for NP discharge treatment unitsare primarily due to the NP irregular periodicity.At present the ma<strong>in</strong> sources of urban NP discharge pollution are sediment<strong>in</strong>gaerosols, destruction of road cover<strong>in</strong>gs, tyres attrition, <strong>and</strong> soil erosion. If erosionproducts were reduced to average values, then pollut<strong>in</strong>g loads of the aerosolcomponent would amount to 58% for cities <strong>and</strong> to 78% for towns. Products of roadcover<strong>in</strong>g destruction amount to 10–25 %.Investigation of dispersive <strong>and</strong> dynamic characteristics of urban aerosols obta<strong>in</strong>eddata on SS concentration <strong>in</strong> NP discharge produced by the design ra<strong>in</strong> under variousdegrees of dust content <strong>in</strong> the air (see Table).The table data demonstrate that reduction of dust content <strong>in</strong> the lower atmosphere,primarily <strong>in</strong> areas with heavy pollut<strong>in</strong>g <strong>in</strong>dustries, can alone cut SS wash-off byseveral times. Such an approach is economically viable.Accord<strong>in</strong>g to our calculations capital costs of 1kg of dust removal from the air isabout 85-fold cheaper than 1 kg of SS removal at a partially separate system unitfor NP discharge treatment <strong>and</strong> about 16-fold cheaper than removal <strong>in</strong> lagoons.Prognostication demonstrated that at the normative air dust content 0.15 mg/m,prevention by simple measures of soil wash-off from lawns <strong>and</strong> open areas, aridhigher durability of road covers can reduce by 30% the total wash-off of pollutantscaused by the design ra<strong>in</strong>.Application of environment protect<strong>in</strong>g <strong>and</strong> technical measures reduc<strong>in</strong>g technogenicpollut<strong>in</strong>g loads <strong>in</strong> urban NP discharge will allow cuts <strong>in</strong> treatment costs of 33–70 %,<strong>and</strong> <strong>in</strong> some cases, with a large discharge of the stream, will completely obviatethem.ConclusionsIntroduction of limits on build up of f<strong>in</strong>e-gra<strong>in</strong>ed particles on urban territories is apromis<strong>in</strong>g way for environmental improvement as a whole <strong>in</strong> all media, <strong>in</strong>clud<strong>in</strong>gwater bodies. If exist<strong>in</strong>g environmental protection measures do not reduce total

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