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User Guide to Thresholds and Classification - Environmental ...

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336<strong>User</strong> <strong>Guide</strong> for <strong>Thresholds</strong> <strong>and</strong> <strong>Classification</strong>sassessment if no experimentally derived data are available. CLOGP, LOGKOW, <strong>and</strong> AUTOLOGP are basedupon the addition of group contributions, while SPARC is based upon a more fundamental chemicalstructure algorithm. SPARC can only be employed in a general way for inorganic or organometalliccompounds. Special methods are needed for estimating log KOW for surface-active compounds, chelatingcompounds <strong>and</strong> mixtures. CLOGP is recommended in the USEPA/EC joint project on validation of QSARestimation methods. Pedersen et al (1995) recommended the CLOGP <strong>and</strong> the LOGKOW programs forclassification purposes because of their reliability, commercial availability, <strong>and</strong> convenience of use. Theestimation methods in Table 19D.2 are recommended for classification purposes.Table 19D.2: Recommended Quantitative Structure Activity Relationships (QSARs) for estimating the n-octanolwaterpartition coefficient (K OW)Model Log K OW range Substance utilityCLOGP 0 < log K OW < 9 * The program calculates log K OW for organic compounds containingC, H, N, O, Hal, P, <strong>and</strong>/or S.LOGKOW(KOWWIN)The program calculates log K OW for organic compounds containing-4 < log K OW < 8 † C, H, N, O, Hal, Si, P, Se, Li, Na, K, <strong>and</strong>/or Hg. Some surfactants(eg, alcohol ethoxylates, dyestuffs, <strong>and</strong> dissociated substances)may be predicted by the program as well.AUTOLOGP. log K OW > 5The program calculates log K OW for organic compounds containingC, H, N, O, Hal, P, <strong>and</strong> S. Improvements are in progress in order<strong>to</strong> extend the program‘s applicability.SPARCProvides improvedresults overKOWWIN <strong>and</strong>CLOGP forcompounds withlog K OW > 5The program is a mechanistic model based on chemicalthermodynamic principles rather than a deterministic model rootedin knowledge obtained from observational data. Therefore,SPARC differs from models that use QSARs (ie, KOWWIN,CLOGP, <strong>and</strong> AUTOLOGP) in that no measured log K OW data areneeded for a training set of chemicals. Only SPARC can be usedin a general way for inorganic or organometallic compounds.Notes* A validation study performed by Niemelä, who compared experimental determined log KOW values withestimated values, showed that the program precisely predicts the log KOW for a great number of organicchemicals in the log KOW range from below 0 <strong>to</strong> above 9 (n = 501, r2 = 0.967) (Pedersen et al, 1995, p 581).† Based on a scatter plot of estimated compared with experimental log KOW (Syracuse Research Corporation,1999), where 13,058 compounds have been tested, the LOGKOW is evaluated being valid for compoundswith a log KOW in the interval -4–8.Chemical classes that need special attention with respect <strong>to</strong> the bioconcentration fac<strong>to</strong>r<strong>and</strong> octanol-water-partition coefficient valuesThere are certain physico-chemical properties, which can make the determination of the BCF or itsmeasurement difficult. These may be substances, which do not bioconcentrate in a manner consistent withtheir other physico-chemical properties, for example, steric hindrance or substances that make the use ofJanuary 2012 EPA0109

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