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User Guide to Thresholds and Classification - Environmental ...

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337<strong>User</strong> <strong>Guide</strong> for <strong>Thresholds</strong> <strong>and</strong> <strong>Classification</strong>sdescrip<strong>to</strong>rs inappropriate, for example, surface activity, which makes both the measurement <strong>and</strong> use of logK OW inappropriate.Difficult substancesSome chemical substances are difficult <strong>to</strong> test in aquatic systems <strong>and</strong> guidance has been developed <strong>to</strong>assist in testing these materials (OECD, 2000). This document is a good source of information on the typesof substances that are difficult <strong>to</strong> test for bioconcentration <strong>and</strong> the steps needed <strong>to</strong> ensure valid conclusionsfrom tests with these substances. Difficult <strong>to</strong> test substances may be poorly soluble, volatile, or subject <strong>to</strong>rapid degradation due <strong>to</strong> such processes as pho<strong>to</strong>transformation, hydrolysis, oxidation, or biotic degradation.To bioconcentrate organic compounds, a substance needs <strong>to</strong> be soluble in lipids, present in the water, <strong>and</strong>available for transfer across the fish gills. Properties that alter this availability will thus change the actualbioconcentration of a substance, when compared with the prediction. For example, readily biodegradablesubstances may only be present in the aquatic compartment for short periods. Similarly, volatility, <strong>and</strong>hydrolysis will reduce the concentration <strong>and</strong> the time during which a substance is available forbioconcentration. A further important parameter, which may reduce the actual exposure concentration of asubstance, is adsorption, either <strong>to</strong> particulate matter or <strong>to</strong> surfaces in general. There are a number ofsubstances, which have shown <strong>to</strong> be rapidly transformed in the organism, thus leading <strong>to</strong> a lower BCF valuethan expected. Substances that form micelles or aggregates may bioconcentrate <strong>to</strong> a lower extent thanwould be predicted from simple physico-chemical properties. This is also the case for hydrophobicsubstances that are contained in micelles formed as a consequence of the use of dispersants. Therefore, theuse of dispersants in bioaccumulation tests is discouraged.In general, for difficult <strong>to</strong> test substances, measured BCF <strong>and</strong> KOW values – based on the parent substance– are a prerequisite for the determination of the bioconcentration potential. Furthermore, properdocumentation of the test concentration is a prerequisite for the validation of the given BCF value.Poorly soluble <strong>and</strong> complex substancesSpecial attention should be paid <strong>to</strong> poorly soluble substances. Frequently the solubility of these substancesis recorded as less than the detection limit, which creates problems in interpreting the bioconcentrationpotential. For such substances the bioconcentration potential should be based on experimentaldetermination of log K OW or QSAR estimations of log K OW . When a multi-component substance is not fullysoluble in water, it is important <strong>to</strong> attempt <strong>to</strong> identify the components of the mixture as far as practicallypossible <strong>and</strong> <strong>to</strong> examine the possibility of determining its bioaccumulation potential using availableinformation on its components. When bioaccumulating components constitute a significant part of thecomplex substance (for example, more than 20% or for hazardous components an even lower content), thecomplex substance should be regarded as being bioaccumulating.High molecular weight substancesAbove certain molecular dimensions, the potential of a substance <strong>to</strong> bioconcentrate decreases. This ispossibly due <strong>to</strong> steric hindrance of the passage of the substance through gill membranes. It has beenJanuary 2012 EPA0109

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