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Harbour waters

Ahern et al. [386] has observed that organophosphorous compounds are coprecipitated with cobalt and pyrrolidine dithiocarbonate, and suggest that this might be a suitable means of preconcentrating the phosphorus fraction of harbour water prior to analysis by X-ray fluorescence spectrometry. [Pg.425]

Litten, S., McReynolds, D., Swart, J., Estabrooks, F., Hoover, D., Hamilton, C., 2003. Chlorinated dioxin/furans in New York harbour water, wastewater, biota, and sediments. Organohalo. Compd. 62, 169-172. [Pg.369]

Harvey, F. E., S. K. Frape R. J. Drimmie, 1997. Isotopic variations in Hamilton Harbour water as an indicator of Lake Ontario exchange flow. J. Great Lakes Res. 23 169-176. [Pg.398]

S. Palanichamy, S. Maruthamuthu, S.T. Manickam, A. Rajendran. Microfouling of manganese-oxidizing bacteria in Tuticorin harbour waters. Current Science, Vol. 82, No. 7, pp. 865-869, 2002. [Pg.127]

Anonymous (1931). Gould, Richard H. Who s who in engineering 3 502. Lewis New York. Anonymous (1954). Richard H. Gould. Civil Engineering 24(6) 402. P Anonymous (1969). R.H. Gould. Journal Water Pollution Control Federation 41(10) 1816. P Gould, R.H. (1922). The area of water surface as a controlling factor in the condition of polluted harbour waters. Trans. ASCE 85 699-737. [Pg.358]

Palanichamy S, Mamthamuthu S, Manickam ST, Rajendran A (2002) MicrofouUng of manganese-oxidizing bacteria in tuticorin harbour waters. Current Science 82(7) 865-86 Critchley M, Taylor R, O HaUoran R (2005) Microbial contribution to blue water corrosion Mater Perform 44(6) 56-59... [Pg.130]

Different real water samples were analyzed by the proposed methods river water, sea water, sewage water and harbour water. All samples were collected at different points of the coast of the Comunidad Valenciana (Spain). Samples were filtered through 0.45 pm nylon membranes (Teknokroma) after their arrival at the laboratory in order to remove any particulate matter. Each sample was analyzed in triplicate and all assays were carried out at ambient temperature. [Pg.561]

Figure 7. Chromatograms obtained for real water samples (a) harbour water sample by the CS-capillary LC-UV(DAD) method (b) sewage water by the IT-SPME-capillary LC-DAD, and (c) sewage water (up) and standard mixture of the tested PAHs (down) by the IT-SPME-LC-FLD methods. Inset comparison of the UV spectra obtained for the sample (—) and for a standard solution of naphthalene (—). For other details, see text. [Pg.572]

Sewage duties, industrial slurries and ash handling De-watering of dirty water when building roads, dams, harbours, tunnels, etc. [Pg.174]

Corrosion problems that arise are frequently discussed under the headings (a) sea-water, and (b) fresh waters, but there is, in fact, no sharp dividing line, since some harbour, estuarine and brackish well waters are mixtures of sea-water and fresh water and are often variable in composition. In the past, corrosion problems were serious, particularly in sea-water service, but resistant alloys have been developed and although trouble still occasionally arises this is more frequently due to poor design or operation rather than to lack of materials suitable for the application. [Pg.694]

Fig. 4.40 Corrosion of Monel 400 in sea-water at Port Hueneme Harbour, Cal., USA (after... Fig. 4.40 Corrosion of Monel 400 in sea-water at Port Hueneme Harbour, Cal., USA (after...
Miscellaneous There are many interesting applications that arise from time to time that are outside the main stream of industry described above. Examples include desalination plant reactor cooling water circuits automobile body corrosion in situ) marine (vessels, piling, harbour installations) aircraft (in situ) packaging and cavitation monitoring. [Pg.1149]

Langston, W.J., Bnrt, G.R., and Mingjiang, Z. (1987). Tin and organotin in water, sediments, and benthic organisms of Poole Harbour. Marine Pollution Bulletin 18, 634—639. [Pg.357]

Abstract. Newly established residential area in Vastra Hamnen (West Harbour) in the city of Malmo uses Aquifer Thermal Energy Storage (ATES) as part of the district heating and cooling system. ATES system has 5 warm and 5 cold wells that are 70-80 m deep. Cold from the nearby sea (Oresund) and water cold from heat pump is stored from winter to summer. The purpose of the system is to deliver free cooling to district cooling system at a temperature level below +6-8 °C. Operational experiences and economic aspects are discussed. [Pg.235]

Mayers IT, Beveridge TJ (1989) The sorption of metals to Bacillus subtilis walls from dilute solutions and simulated Hamilton harbour (Lake Ontario) water. Can J Microbiol 35 764-770... [Pg.96]

Kerkhoff, M. and J.D. Boer. 1982. Identification of chlordane compounds in harbour seals from the coastal waters of the Netherlands. Chemosphere 11 841-845. [Pg.881]

Lake Erie, Hamilton Harbour 1984 Water column vs. sediments ... [Pg.1277]

Kleivane, L., J.U. Skaare, A. Bjorge, E. de Ruiter, and P.J.H. Reijnders. 1995. Qrganochlorine pesticide residue and PCBs in harbour porpoise (Phocoena phocoena) incidentally caught in Scandinavian waters. Environ. Pollut. 89 137-146. [Pg.1331]

Mudroch, A., F.I. Onuska, and L. Kalas. 1989. Distribution of polychlorinated biphenyls in water, sediments, and biota of two harbours. Chemosphere 18 2141-2154. [Pg.1333]

Law, R.J. and J.A. Whinnett. 1992. Polycyclic aromatic hydrocarbons in muscle tissue of harbour porpoises (Phocoena phocoena) from UK waters. Mar. Pollut. Bull. 24 550-553. [Pg.1402]


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See also in sourсe #XX -- [ Pg.197 ]




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