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Surface Water Abstraction Directive

Abstract This chapter discusses disposal to surface water, the most common method of concentrate management. This includes concentrate that is directly disposed of into rivers, creeks, lakes, oceans, bays, and other bodies of water. Concentrate is piped to the site of disposal, where it is discharged to the receiving body of water via an outfall structure. The environmental impacts of surface water disposal may be lessened by diluting the concentrate prior to discharge, or by dilution of the concentrate through the design of the outfall strucmre and diffusers. Pretreatment processes that lessen the impact on the environment should also be considered. [Pg.30]

The Council directive concerning the quality required of surface water intended for the abstraction of drinking-water in the Member States 75/440/EEC of 16 June 1975 lays down mandatory levels of phenols, dissolved or emulsified hydrocarbons, polycyclic aromatic hydrocarbons, total pesticides (parathion, BHC, dieldrin) which the treated waters must reach after application of the appropriate treatment. [Pg.242]

The first generation of EU water legislation consisted of more or less isolated pieces of legislation, with little or no cross-referencing. The previous DWD 80/778/EEC only makes reference to one piece of EU legislation, namely the Council Directive on the Quality of Surface Water, intended for the abstraction of Drinking Water (75/440/EEC). The current DWD refers to a number of other directives that are related to the original directive or have interactions with that directive ... [Pg.5]

There are several properties of a chemical that are related to exposure potential or overall reactivity for which structure-based predictive models are available. The relevant properties discussed here are bioaccumulation, oral, dermal, and inhalation bioavailability and reactivity. These prediction methods are based on a combination of in vitro assays and quantitative structure-activity relationships (QSARs) [3]. QSARs are simple, usually linear, mathematical models that use chemical structure descriptors to predict first-order physicochemical properties, such as water solubility. Other, similar models can then be constructed that use the first-order physicochemical properties to predict more complex properties, including those of interest here. Chemical descriptors are properties that can be calculated directly from a chemical structure graph and can include abstract quantities, such as connectivity indices, or more intuitive properties, such as dipole moment or total surface area. QSAR models are parameterized using training data from sets of chemicals for which both structure and chemical properties are known, and are validated against other (independent) sets of chemicals. [Pg.23]

Hydrogen. The reaction of O ( D2) with H2 takes place on the ground state potential surface of water, HiOf Ai). On the basis of trajectory calculations, (Whitlock et al., 1982) it has been suggested that, as is true for the hydrocarbons, parallel mechanisms involving insertion/elimination and direct abstraction govern the course of this reaction. The observation using laser induced fluorescence spectroscopy (Luntz et al., 1979 Smith and Butler, 1980) of a highly excited, non-Boltzmann rotational distribution and a nearly statistical vibrational distribution for v" = 1 and v" = 0 is consistent with the insertion/elimination... [Pg.167]

Abstract. Polymerization in direct mini-emulsions is a relatively new polymerization technique which allows the preparation of submicron latex particles within the range 100large population of submicron monomer droplets in water (termed the mini-emulsion) by intensive shear force with the aid of an adequate emulsifier and coemulsifier (or hydrophobe). These stable, homogenized monomer droplets have an extremely large surface area and, therefore, can compete effectively with the monomer-swollen micelles, if present, for the oligomeric radicals gen-... [Pg.101]


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See also in sourсe #XX -- [ Pg.19 ]




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