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User Guide to Thresholds and Classification - Environmental ...

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380<strong>User</strong> <strong>Guide</strong> for <strong>Thresholds</strong> <strong>and</strong> <strong>Classification</strong>s<strong>Environmental</strong> fac<strong>to</strong>rs<strong>Environmental</strong> parameters influencing the physiology of the organism may also affect the uptake ofsubstances. For instance, when the oxygen content of the water is lowered, fish have <strong>to</strong> pass more waterover their gills in order <strong>to</strong> meet respira<strong>to</strong>ry dem<strong>and</strong>s (McKim <strong>and</strong> Goeden, 1982). However, there may bespecies dependency as indicated by Opperhuizen <strong>and</strong> Schrap (1987). It has, furthermore, been shown thatthe temperature may have an influence on the uptake rate constant for lipophilic substances (Sijm et al,1993), whereas other authors have not found any consistent effect of temperature changes (Black et al,1991).Fac<strong>to</strong>rs influencing the elimination rateThe elimination rate is mainly a function of the size of the organism, the lipid content, the biotransformationprocess of the organism, <strong>and</strong> the lipophilicity of the test compound.Size of organismAs for the uptake rate the elimination rate is dependent on the size of the organism. Due <strong>to</strong> the higher gillsurface <strong>to</strong> weight ratio for small organisms (for example, fish larvae) than that of large organisms, steadystate<strong>and</strong> thus ‗<strong>to</strong>xic dose equilibrium‘ has shown <strong>to</strong> be reached sooner in early life stages than injuvenile/adult stages of fish (Petersen <strong>and</strong> Kristensen, 1998). As the time needed <strong>to</strong> reach steady-stateconditions is dependent on k2, the size of fish used in bioconcentration studies has thus an importantbearing on the time required for obtaining steady-state conditions.Lipid contentDue <strong>to</strong> partitioning relationships, organisms with a high fat content tend <strong>to</strong> accumulate higher concentrationsof lipophilic substances than lean organisms under steady-state conditions. Body burdens are therefore oftenhigher for ‗fatty‘ fish such as eel, compared <strong>to</strong> ‗lean‘ fish such as cod. In addition, lipid ‗pools‘ may act ass<strong>to</strong>rage of highly lipophilic substances. Starvation or other physiological changes may change the lipidbalance <strong>and</strong> release such substances <strong>and</strong> result in delayed impacts.MetabolismIn general, metabolism or biotransformation leads <strong>to</strong> the conversion of the parent compound in<strong>to</strong> morewater-soluble metabolites. As a result, the more hydrophilic metabolites may be more easily excreted fromthe body than the parent compound. When the chemical structure of a compound is altered, many propertiesof the compound are altered as well. Consequently the metabolites will behave differently within theorganism with respect <strong>to</strong> tissue distribution, bioaccumulation, persistence, <strong>and</strong> route <strong>and</strong> rate of excretion.Biotransformation may also alter the <strong>to</strong>xicity of a compound. This change in <strong>to</strong>xicity may either be beneficialor harmful <strong>to</strong> the organism. Biotransformation may prevent the concentration in the organism from becomingso high that a <strong>to</strong>xic response is expressed (de<strong>to</strong>xification). However, a metabolite may be formed which ismore <strong>to</strong>xic than the parent compound (bioactivation) as known for, for example, benzo(a)pyrene.Terrestrial organisms have a developed biotransformation system, which is generally better than that oforganisms living in the aquatic environment. The reason for this difference may be the fact thatJanuary 2012 EPA0109

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