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Sewage contamination

Hepatitis A virus (HAV) Naked icosahedra 27 nm in diameter Responsible for infectious hepatitis spread by the oro-faecal route especially in children. Also associated with sewage contamination of food or water supplies... [Pg.65]

Consequences of repeated applications of sewage contaminated with organic compounds to land... [Pg.22]

USEPA. Development Document for Effluent Limitation Guidelines and New Source Performance Standards for the Tire and Synthetic Segment of the Rubber Processing Point Source Category, U.S. Environmental Protection Agency Washington, DC. http //www.epa.gov/cgi-bin/, 1974. Morzycki, J. Effluents from sewage contaminated with latex. Chem. Ahs. 1966, 64, 3192. [Pg.579]

Gerba, C. P., Wallis, C., and Melnick, J. L. (1977a). Application of photodynamic oxidation to the disinfection of tapwater, seawater, and sewage contaminated with poliovirus. Photochem. Photobiol. 26, 499-504. [Pg.145]

Rogers, K. (1999). Effects of sewage contamination on macro-al e and shellfish at Moa Point, New Zealand using stable carbon and nitrogen isotopes. N. Z..J. Mar. Freshw. Res. 33, 181—188. RusseU, B. D., and ConneU, S. D. (2005). A novel interaction between nutrients and grazers alters relative dominance of marine habitats. Mar. Ecol. Prog. Ser. 289, 5—11. [Pg.945]

Valiela, I., Teal,. M., Cogswell, C., Hartman,., AUen, S., Van Etten, R., and Goehringer, D. (1985b). Some long-term consequences of sewage contamination in salt marsh ecosystems. In Ecological Considerations in Wedand Treatment of Municipal Wastewaters (Godfrey, P.., Kaynor, E. R., Pelczarski, S., and Benforado,., eds.). Van Nostrand-Reinhold, New York, pp. 301-316. [Pg.1035]

Simulation of phosphate transport in sewage-contaminated groundwater, Cape Cod, Massachusetts Applied Geochemistry, v. 11, p. 317-324. [Pg.462]

Chemical analysis for specific redox couples is especially useful in studies of groundwaters contaminated by waste disposal, where redox gradients are often steep, and the fate of redox-sensitive contaminants may be rate dependent or otherwise unpredictable. In such a study of sewage-contaminated groundwaters, Kent et al. (1994) found that reduction of O2, Cr(VI), and Se(VI) did not occur, although it was thermodynamically favored. They concluded that the disequilbrium resulted from unfavorable microbial conditions and heterogeneity of groundwater flow. [Pg.415]

Krueger CJ, Barber LB, Metge DW (1998) fate and transport of linear alkylbenzensulfonates in a sewage-contaminated aquifer A comparison of natural-gradient pulsed tracer tests. Environ Sci Technol 32, 1134-1142. [Pg.429]

D. R. LeBlanc in Movement and Fate of Solute Transport in a Plume of Sewage-Contaminated Ground Water, Cape Cod, Massachusetts, United States Geological Survey Open File Report, USGS, Virginia, 1984, pp. 11-45. [Pg.10]

Sorption of Mo(VI) in these experiments can be described by the Freundlich isotherm. Freundlich constants for sorption from sewage-contaminated ground water were calculated from a linear plot of the concentration of Mo(VI) sorbed by sediment in each column compared to input concentration (Figure 1) using the following equation ... [Pg.244]

Figure 1. Freundlich plot of Mo(VI) sorption parameters for sewage-contaminated ground water and uncontaminated ground water. The size of plotted experimental data points in all Figures encompasses the analytical error. Figure 1. Freundlich plot of Mo(VI) sorption parameters for sewage-contaminated ground water and uncontaminated ground water. The size of plotted experimental data points in all Figures encompasses the analytical error.

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See also in sourсe #XX -- [ Pg.342 ]

See also in sourсe #XX -- [ Pg.1518 ]




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