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User Guide to Thresholds and Classification - Environmental ...

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375<strong>User</strong> <strong>Guide</strong> for <strong>Thresholds</strong> <strong>and</strong> <strong>Classification</strong>sLog n-octanol-water partition coefficientDefinition <strong>and</strong> general considerationsThe log K OW is a measure of the lipophilicity of a substance. As such, log K OW is a key parameter in theassessment of environmental fate. Many distribution processes are driven by log K OW , for example, sorption<strong>to</strong> soil <strong>and</strong> sediment <strong>and</strong> bioconcentration in organisms.The basis for the relationship between bioconcentration <strong>and</strong> log K OW is the analogy for the partition processbetween the lipid phase of fish <strong>and</strong> water <strong>and</strong> the partition process between n-octanol <strong>and</strong> water. The reasonfor using KOW arises from the ability of octanol <strong>to</strong> act as a satisfac<strong>to</strong>ry surrogate for lipids in fish tissue.Highly significant relationships between log KOW <strong>and</strong> the solubility of substances in cod liver oil <strong>and</strong> triolinexist (Niimi, 1991). Triolin is one of the most abundant triacylglycerols found in freshwater fish lipids(Henderson <strong>and</strong> Tocher, 1987).The determination of the n-octanol-water partition coefficient (KOW) is a requirement of the base data set <strong>to</strong>be submitted for notified new <strong>and</strong> priority existing substances within the European Union (EU). As theexperimental determination of the KOW is not always possible, for example, for very water-soluble <strong>and</strong> forvery lipophilic substances, a Quantitative Structure Activity Relationship (QSAR) derived KOW may be used.However, extreme caution should be exercised when using QSARs for substances where the experimentaldetermination is not possible (as for, for example, surfactants).Appropriate methods for experimental determination of KOW valuesFor experimental determination of KOW values, two different methods, Shake-flask <strong>and</strong> High PerformanceLiquid Chroma<strong>to</strong>graphy (HPLC), have been described in st<strong>and</strong>ard guidelines for example, OECD 107 <strong>and</strong>OECD 117. For highly lipophilic substances, which are slowly soluble in water, data obtained by employing aslow-stirring method are generally more reliable (De Bruijn et al, 1989; Tolls <strong>and</strong> Sijm, 1993; OECD Test<strong>Guide</strong>line 123, 2006).Shake-flask methodThe basic principle of the method is <strong>to</strong> measure the dissolution of the substance in two different phases,water <strong>and</strong> n-octanol. In order <strong>to</strong> determine the partition coefficient, equilibrium between all interactingcomponents of the system must be achieved after which the concentration of the substances dissolved in thetwo phases is determined. The shake-flask method is applicable when the log KOW value falls within therange from -2 <strong>to</strong> 4 (OECD 107, 1995). The shake-flask method applies only <strong>to</strong> essential pure substancessoluble in water <strong>and</strong> n-octanol <strong>and</strong> should be performed at a constant temperature (±1ºC) in the range 20–25ºC.High Performance Liquid Chroma<strong>to</strong>graphy methodHPLC is performed on analytical columns packed with a commercially available solid phase containing longhydrocarbon chains (for example, C8, C18) chemically bound on<strong>to</strong> silica. Chemicals injected on<strong>to</strong> such acolumn move along at different rates because of the different degrees of partitioning between the mobileaqueous phase <strong>and</strong> the stationary hydrocarbon phase. The HPLC method is not applicable <strong>to</strong> strong acidsJanuary 2012 EPA0109

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