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Fish, bioconcentration factors

Chiou, C. T. (1985) Partition coefficients of organic compounds in lipid-water systems and correlations with fish bioconcentration factors. Environ. Sci. Technol. 19, 57-62. [Pg.50]

Hawker, D. W. (1990a) Vapor pressures and Henry s law constants of polychlorinated biphenyls. Environ. Sci. Technol. 23, 1250-1253. Hawker, D. W. (1990b) Description of fish bioconcentration factors in terms of solvatochromic parameters. Chemosphere 20, 267-477. Hawker, D. W., Connell, D. W. (1988) Octanol-water partition coefficients of polychlorinated biphenyl congeners. Environ. Sci. Technol. 22, 382-387. [Pg.52]

Hawker, D.W. (1990) Description of fish bioconcentration factors in terms of solvatochromic parameters. Chemosphere 20, 467 -77. [Pg.907]

Lu, X., Tao, S., Cao, J., Dawson, R.W. (1999) Prediction of fish bioconcentration factors of nonpolar organic pollutants based on molecular connectivity indices. Chemosphere 39, 987-999. [Pg.909]

Laskowski [1] has thoroughly reviewed the physico-chemical properties of the SPs, and these are summarized briefly below. SPs are typically of low water solubility (in the low microgram per liter range) and are highly nonpolar (logarithmic octanol water partition coefficients of around 6-7), indicating potential for bioaccumulation. Fish bioconcentration factors (BCF) of several hundred to several thousand are reported however metabolism limits the amount of bioaccumulation,... [Pg.138]

Table 7 Example application of process in Box B to evaluate the risk of dioxins in Dutch sediments. No observed effect (NOEC) concentrations for chronic toxicity of dioxins in vertebrates (immune, reproductive and developmental toxicity) expressed as internal concentration (ng TEQ/g Iw). The sediment to fish bioconcentration factor is set at 4 (ng TEQ/g Organic Carbon to ng/g lipid weight in fish) based on Traas et al. (2001). Based on a species-specific biomagnification factor (BMP) from fish to animal (ng TEQ/g Iw) the internal NOEC is extrapolated to a NOEC in sediment. These data are used to construct the SSDs in Figures 5 and 6. Table 7 Example application of process in Box B to evaluate the risk of dioxins in Dutch sediments. No observed effect (NOEC) concentrations for chronic toxicity of dioxins in vertebrates (immune, reproductive and developmental toxicity) expressed as internal concentration (ng TEQ/g Iw). The sediment to fish bioconcentration factor is set at 4 (ng TEQ/g Organic Carbon to ng/g lipid weight in fish) based on Traas et al. (2001). Based on a species-specific biomagnification factor (BMP) from fish to animal (ng TEQ/g Iw) the internal NOEC is extrapolated to a NOEC in sediment. These data are used to construct the SSDs in Figures 5 and 6.
Whole fish, bioconcentration factor of 344 Acrolein not detected in tissues major metabolites were 1,3-propanediol and glyceric acid... [Pg.756]

Sabljic, A., The prediction of fish bioconcentration factors of organic pollutants from the molecular connectivity model, Zeitschrift Fiir die Gesamte Hygiene und ihre Grenzgebiete, 33, 493-496, 1987. [Pg.359]

Detected in water, sludge, sediment, algae, mussel, or fish. Bioconcentration factor (BCF)... [Pg.39]

See other pages where Fish, bioconcentration factors is mentioned: [Pg.255]    [Pg.705]    [Pg.756]    [Pg.1045]    [Pg.262]    [Pg.107]    [Pg.112]    [Pg.122]    [Pg.705]    [Pg.1045]    [Pg.255]    [Pg.359]    [Pg.44]    [Pg.446]   
See also in sourсe #XX -- [ Pg.138 ]



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