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User Guide to Thresholds and Classification - Environmental ...

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379<strong>User</strong> <strong>Guide</strong> for <strong>Thresholds</strong> <strong>and</strong> <strong>Classification</strong>s19F.3 Influence of external <strong>and</strong> internal fac<strong>to</strong>rs on the bioconcentrationpotential of organic substancesFac<strong>to</strong>rs influencing the uptakeThe uptake rate for lipophilic compounds is mainly a function of the size of the organism (Sijm <strong>and</strong> Linde,1995). External fac<strong>to</strong>rs such as the molecular size, fac<strong>to</strong>rs influencing the bioavailability, <strong>and</strong> differentenvironmental fac<strong>to</strong>rs are of great importance <strong>to</strong> the uptake rate as well.Size of organismSince larger fish have a relatively lower gill surface <strong>to</strong> weight ratio, a lower uptake rate constant (k1) is <strong>to</strong> beexpected for large fish compared <strong>to</strong> small fish (Opperhuizen <strong>and</strong> Sijm, 1990; Sijm <strong>and</strong> Linde, 1995). Theuptake of substances in fish is further controlled by the water flow through the gills; the diffusion throughaqueous diffusion layers at the gill epithelium; the permeation through the gill epithelium; the rate of bloodflow through the gills, <strong>and</strong> the binding capacity of blood constituents (ECETOC, 1995).Molecular sizeIonised substances do not readily penetrate membranes; as aqueous pH can influence the substanceuptake. Loss of membrane permeability is expected for substances with a considerable cross sectional area(Anliker et al, 1988; Opperhuizen et al, 1985) or long chain length (> 4.3 nm) (Opperhuizen, 1986). Loss ofmembrane permeability due <strong>to</strong> the size of the molecules will thus result in <strong>to</strong>tal loss of uptake. The effect ofmolecular weight on bioconcentration is due <strong>to</strong> an influence on the diffusion coefficient of the substance,which reduces the uptake rate constants (Gobas et al, 1986).AvailabilityBefore a substance is able <strong>to</strong> bioconcentrate in an organism it needs <strong>to</strong> be present in water <strong>and</strong> available fortransfer across fish gills. Fac<strong>to</strong>rs, which affect this availability under both natural <strong>and</strong> test conditions, will alterthe actual bioconcentration in comparison <strong>to</strong> the estimated value for BCF. As fish are fed duringbioconcentration studies, relatively high concentrations of dissolved <strong>and</strong> particulate organic matter may beexpected, thus reducing the fraction of chemical that is actually available for direct uptake via the gills.McCarthy <strong>and</strong> Jimenez (1985) have shown that adsorption of lipophilic substances <strong>to</strong> dissolved humicmaterials reduces the availability of the substance, the more lipophilic the substance the larger reduction inavailability (Schrap <strong>and</strong> Opperhuizen, 1990). Furthermore, adsorption <strong>to</strong> dissolved or particulate organicmatter or surfaces in general may interfere during the measurement of BCF (<strong>and</strong> other physical/chemicalproperties) <strong>and</strong> thus make the determination of BCF or appropriate descrip<strong>to</strong>rs difficult. As bioconcentrationin fish is directly correlated with the available fraction of the chemical in water, it is necessary for highlylipophilic substances <strong>to</strong> keep the available concentration of the test chemical within relatively narrow limitsduring the uptake period. Substances, which are readily biodegradable, may only be present in the test waterfor a short period, <strong>and</strong> bioconcentration of these substances may thus be insignificant. Similarly, volatility<strong>and</strong> hydrolysis will reduce the concentration <strong>and</strong> time in which the substance is available forbioconcentration.January 2012 EPA0109

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