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Polychlorinated biphenyls marine

Billsson, K., Westerlund, L., Tysklind, M., and Olsson, P.-E. (1998). Developmental disturbances caused by polychlorinated biphenyls in zebrafish (Brachydanio rerio). Marine Environmental Research 46, 461 64. [Pg.339]

Borlakogln, J.T., Wilkins, J.P.G., and Walker, C.H. (1988). Polychlorinated biphenyls in sea birds—molecnlar features and metabolic interpretations. Marine Environmental Research 24, 15-19. [Pg.340]

Kannan, N., S. Tanabe, M. Ono, and R. Tatsukawa. 1989. Critical evaluation of polychlorinated biphenyl toxicity in terrestrial and marine mammals increasing impact of non-ortho and mono-ortho coplanar polychlorinated biphenyls from land to ocean. Arch. Environ. Contam. Toxicol. 18 850-857. [Pg.1330]

Kennish, M.J. 1992. Polychlorinated biphenyls in estuarine and coastal marine waters of New Jersey a review of contamination problems. Rev. Aquat. Sci. 6 275-293. [Pg.1330]

Kuehl, D.W., B.C. Butterworth, J. Libal, and P. Marquis. 1991. An isotope dilution high resolution gas chromatographic-high resolution mass spectrometric method for the determination of coplanar polychlorinated biphenyls application to fish and marine mammals. Chemosphere 22 849-858. [Pg.1331]

Muir, D.C.G., R.J. Norstrom, and M. Simon. 1988. Qrganochlorine contaminants in Arctic marine food chains accumulation of specific polychlorinated biphenyls and chlordane-related compounds. Environ. Sci. Technol. 22 1071-1079. [Pg.1334]

Porte, C., D. Barcelo, and J. Albaiges. 1988. Quantitation of total versus selected polychlorinated biphenyl congeners in marine biota samples. Jour. Chromatogr. 442 386-393. [Pg.1335]

A second reason why marine pollution is difficult to measme lies in the large number of pollutants being introduced and the myriad of pathways by which they enter the oceans. In 2006, 82,000 different chemicals were in commercial use, with approximately 1000 new ones being added annually. Most have the potential to reach the ocean. In some cases, groups of these compoimds can be measured in one analysis, such as the PCBs (polychlorinated biphenyls) and PAHs (polycyclic aromatic hydrocarbons). Nevertheless, a large number of analyses are required to measme all the pollutants that can potentially be present in seawater. [Pg.768]

Moser, V.C., Cheek, B.M. MacPhail, R.C. (1995) A multidisciplinary approach to toxicological screening 111. Neurobehavioral toxicity. J. Toxicol environ. Health, 45, 173-210 Miiller-Tegethoff, K., Kasper, P. Muller, L. (1995) Evaluation studies on the in vitro rat hepatocyte micronucleus assay. Mutat. Res., 335, 293-307 Murray, H.E., Ray, L.E Giam, C.S. (1981) Phthalic acid esters, total DDTs and polychlorinated biphenyls in marine samples from Galveston Bay, Texas. Bull, environ. Contam. Toxicol, 26, 769-774... [Pg.139]

Sayler, G.S., Thomas, R. Colwell, R. R. (1978). Polychlorinated biphenyl (PCB) degrading bacteria and PCB in estuarine and marine environments. Estuarine Coastal Marine Science, 6, 553-67. [Pg.250]

DL Hayteas, DA Duffield. Use of high-performance liquid chromatography for the estimation of polychlorinated biphenyls and p,p -DDE residues in marine mammals. J Chromatogr B 705 362-366, 1998. [Pg.757]

Clayton, J.R., S.P. Pavlou, and N.F. Breitner. 1977. Polychlorinated biphenyls in coastal marine zooplankton. Environ. Sci. Technol. 18, 676-682. [Pg.249]

Burgess, R. M., R. A. McKinney, W. A. Brown, J. G. Quinn. 1996. Isolation of marine sediment colloids and associated polychlorinated biphenyls A comparison of ultrafiltration and reverse phase chromatography. Environmental Science and Technology 30 1923. [Pg.180]

Fig. 2.16. Homolog composition (mean%) of polychlorinated biphenyls (PCBs) in (A) freshwater sediment (n = 64), (B) marine sediment (n = 195), and (C) organism (n = 132), from South Korea. Fig. 2.16. Homolog composition (mean%) of polychlorinated biphenyls (PCBs) in (A) freshwater sediment (n = 64), (B) marine sediment (n = 195), and (C) organism (n = 132), from South Korea.
Fig. 2.17. Comparison of measured levels and sediment quality guidelines (SQGs) for total polychlorinated biphenyls (PCBs) in sediments from the various sites, in South Korea (a) freshwater (n = 64), (b) brackish (n = 15), and (c) marine sediments (n = 362). Range indicates minimum (min), maximum (max), and arithmetic mean (avg.). Dotted lines represent SQGs of effect range low (ERL) and effect range median (ERM) for total PCBs (Long et al., 1995). Fig. 2.17. Comparison of measured levels and sediment quality guidelines (SQGs) for total polychlorinated biphenyls (PCBs) in sediments from the various sites, in South Korea (a) freshwater (n = 64), (b) brackish (n = 15), and (c) marine sediments (n = 362). Range indicates minimum (min), maximum (max), and arithmetic mean (avg.). Dotted lines represent SQGs of effect range low (ERL) and effect range median (ERM) for total PCBs (Long et al., 1995).
Kim, S.K., Lee, D.S., Oh, J.R., 2002e. Characteristics of trophic transfer of polychlorinated biphenyls in marine organisms in Incheon North Harbor, Korea. Environ. Toxicol. Chem. 21, 834-841. [Pg.149]


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See also in sourсe #XX -- [ Pg.623 , Pg.625 ]




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Polychlorinated biphenyls

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