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Octanol-water partition coefficient

From Wikipedia, the free encyclopedia
Measure of lipophilicity and hydrophilicity

Then-octanol-water partition coefficient,Kow is apartition coefficient for the two-phase system consisting ofn-octanol and water.[1]Kow is also frequently referred to by the symbol P, especially in the English literature. It is also calledn-octanol-water partition ratio.[2][3][4]

Kow serves as a measure of the relationship betweenlipophilicity (fat solubility) andhydrophilicity (water solubility) of a substance. The value is greater than one if a substance is more soluble in fat-like solvents such as n-octanol, and less than one if it is more soluble in water.[citation needed]

If a substance is present as severalchemical species in the octanol-water system due toassociation ordissociation, each species is assigned its ownKow value. A related value, D, does not distinguish between different species, only indicating the concentration ratio of the substance between the two phases.[citation needed]

History

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In 1899,Charles Ernest Overton andHans Horst Meyer independently proposed that the tadpole toxicity of non-ionizable organic compounds depends on their ability to partition into lipophilic compartments of cells. They further proposed the use of the partition coefficient in an olive oil/water mixture as an estimate of this lipophilic associated toxicity.Corwin Hansch later proposed the use of n-octanol as an inexpensive synthetic alcohol that could be obtained in a pure form as an alternative to olive oil.[5][6]

Applications

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Kow values are used, among others, to assess the environmental fate ofpersistent organic pollutants. Chemicals with high partition coefficients, for example, tend to accumulate in the fatty tissue of organisms (bioaccumulation). Under theStockholm Convention, chemicals with a logKow greater than 5 are considered to bioaccumulate.[7]

Furthermore, the parameter plays an important role in drug research (Rule of Five) andtoxicology.Ernst Overton andHans Meyer discovered as early as 1900 that theefficacy of an anaesthetic increased with increasingKow value (the so-calledMeyer-Overton rule).[8]

Kow values also provide a good estimate of how a substance is distributed within acell between the lipophilicbiomembranes and the aqueouscytosol.[citation needed]

Estimation

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Since it is not possible to measureKow for all substances, various models have been developed to allow for their prediction, e.g.Quantitative structure–activity relationships (QSAR) orlinear free energy relationships (LFER)[9][10] such as theHammett equation.[9]

A variant of theUNIFAC system can also be used to estimate octanol-water partition coefficients.[11] Under REACH, estimates are often derived byEPI Suite orCOSMOtherm.[12]

Equations

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  • Definition of theKow or P-value
TheKow or P-value always only refers to a singlespecies or substance:
Kow=P=coSicwSi{\displaystyle K_{\mathrm {ow} }=P={\frac {c_{o}^{S_{i}}}{c_{w}^{S_{i}}}}}
with:
If different species occur in the octanol-water system by dissociation or association, several P-values and one D-value exist for the system. If, on the other hand, the substance is only present in a single species, the P and D values are identical.
P is usually expressed as acommon logarithm, i.e. Log P (also Log Pow or, less frequently, Log pOW):
logP=logcoSicwSi=logcoSilogcwSi{\displaystyle \log {P}=\log {\frac {c_{o}^{S_{i}}}{c_{w}^{S_{i}}}}=\log c_{o}^{S_{i}}-\log c_{w}^{S_{i}}} Log P is positive for lipophilic and negative for hydrophilic substances or species.
  • Definition of the D-value
The P-value only correctly refers to the concentration ratio of a single substance distributed between the octanol and water phases. In the case of a substance that occurs as multiple species, it can therefore be calculated by summing the concentrations of alln species in the octanol phase and the concentrations of alln species in the aqueous phase:
D=cocw=coS1+coS2++coSncwS1+cwS2++cwSn{\displaystyle D={\frac {c_{o}}{c_{w}}}={\frac {c_{o}^{S_{1}}+c_{o}^{S_{2}}+\dots +c_{o}^{S_{n}}}{c_{w}^{S_{1}}+c_{w}^{S_{2}}+\dots +c_{w}^{S_{n}}}}}
with:
D values are also usually given in the form of the common logarithm as Log D:
logD=logcocw=logcologcw{\displaystyle \log {D}=\log {\frac {c_{o}}{c_{w}}}=\log c_{o}-\log c_{w}}
Like Log P, Log D is positive for lipophilic and negative for hydrophilic substances. While P values are largely independent of thepH value of the aqueous phase due to their restriction to only one species, D values are often strongly dependent on the pH value of the aqueous phase.

Example values

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Values for logKow typically range between -3 (very hydrophilic) and +10 (extremely lipophilic/hydrophobic).[13]

The values listed here[14] are sorted by the partition coefficient. Acetamide is hydrophilic, and 2,2′,4,4′,5-Pentachlorobiphenyl is lipophilic.

SubstancelogKOWTReference
Acetamide−1.15525 °C
Methanol−0.82419 °C
Formic acid−0.41325 °C
Diethyl ether0.83320 °C
p-Dichlorobenzene3.37025 °C
Hexamethylbenzene4.61025 °C
2,2′,4,4′,5-Pentachlorobiphenyl6.410Ambient

See also

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References

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  1. ^Sangster J (1997).Octanol-water partition coefficients : fundamentals and physical chemistry. Chichester: Wiley.ISBN 0-471-97397-1.OCLC 36430034.
  2. ^Mackay D (2021).Multimedia environmental models : the fugacity approach. J. Mark Parnis (Third ed.). Boca Raton, FL.ISBN 978-1-000-09499-2.OCLC 1182869019.{{cite book}}: CS1 maint: location missing publisher (link)
  3. ^Hodges G, Eadsforth C, Bossuyt B, Bouvy A, Enrici MH, Geurts M, et al. (2019)."A comparison of log Kow (n-octanol–water partition coefficient) values for non-ionic, anionic, cationic and amphoteric surfactants determined using predictions and experimental methods".Environmental Sciences Europe.31 (1) 1.doi:10.1186/s12302-018-0176-7.
  4. ^Hendriks AJ, van der Linde A, Cornelissen G, Sijm DT (July 2001). "The power of size. 1. Rate constants and equilibrium ratios for accumulation of organic substances related to octanol-water partition ratio and species weight".Environmental Toxicology and Chemistry.20 (7):1399–420.Bibcode:2001EnvTC..20.1399H.doi:10.1002/etc.5620200703.PMID 11434281.S2CID 25971836.
  5. ^Lipnick RL (1989)."Narcosis, electrophile and proelectrophile toxicity mechanisms: Application of SAR and QSAR".Environmental Toxicology and Chemistry.8 (1):1–2.doi:10.1002/etc.5620080101.
  6. ^Hansch C (June 2011). "The advent and evolution of QSAR at Pomona College".Journal of Computer-aided Molecular Design.25 (6):495–507.Bibcode:2011JCAMD..25..495H.doi:10.1007/s10822-011-9444-y.PMID 21678028.S2CID 1399290.
  7. ^Stockholm Convention on Persistent Organic Pollutents (POPs)(PDF). Geneva: United Nations Environment Programme. 2018. pp. Annex D.{{cite book}}:|work= ignored (help)
  8. ^Evers AS, Crowder M (2009)."Mechanisms of Anesthesia and Consciousness". In Barash PG, Cullen BF, Stoelting RK, Catalan MK, Stock MC (eds.).Clinical Anesthesia. Lippincott Williams & Wilkins. p. 106.ISBN 978-0-7817-8763-5.
  9. ^abDearden JC (September 1985)."Partitioning and lipophilicity in quantitative structure-activity relationships".Environmental Health Perspectives.61:203–28.Bibcode:1985EnvHP..61..203D.doi:10.1289/ehp.8561203.PMC 1568760.PMID 3905374.
  10. ^Kellogg GE, Abraham DJ (July 2000). "Hydrophobicity: is LogP(o/w) more than the sum of its parts?".European Journal of Medicinal Chemistry.35 (7–8):651–61.doi:10.1016/s0223-5234(00)00167-7.PMID 10960181.
  11. ^Gani R, Abildskov J, Kontogeorgis G (2004-06-30)."Application of property models in chemical product design". In Kontogeorgis GM, Gani R (eds.).Computer Aided Property Estimation for Process and Product Design: Computers Aided Chemical Engineering. Elsevier.ISBN 978-0-08-047228-7.
  12. ^Glüge, Juliane; Scheringer, Martin (2023). "Evaluation of Physicochemical Property Data in the ECHA Database".Journal of Physical and Chemical Reference Data.52 (4).doi:10.1063/5.0153030.hdl:20.500.11850/639388.
  13. ^Cumming H, Rücker C (September 2017)."Octanol-Water Partition Coefficient Measurement by a Simple1H NMR Method".ACS Omega.2 (9):6244–6249.doi:10.1021/acsomega.7b01102.PMC 6644330.PMID 31457869.
  14. ^"Dortmund Data Bank (DDB)".Dortmund Data Bank Software & Separation Technology (DDBST) GmbH. Retrieved2020-05-20.

Further reading

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External links

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