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Diss Factsheets
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EC number: 233-713-2 | CAS number: 10326-41-7
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Partition coefficient
Administrative data
Link to relevant study record(s)
- Endpoint:
- partition coefficient
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Justification for type of information:
- This information is used in a read-across approach in the assessment of the target substance. For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Reason / purpose for cross-reference:
- read-across source
- Type:
- log Pow
- Partition coefficient:
- >= -0.72 - <= -0.62
- Temp.:
- 20 °C
- Remarks on result:
- other: Range of values from the publications reviewed
- Conclusions:
- The log Kow of lactic acid as cited in the reviewed publications ranges between -0.72 and -0.62.
- Executive summary:
An overview is given of literature data (measured values) for the log Kow of lactic acid. The reported values consistently range between -0.72 and -0.62. However, documentation of the methodology in the original references is scarce, complicating assessment of the reliability of the individual sources.
This information is used in a read-across approach in the assessment of the target substance. For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Endpoint:
- partition coefficient
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- This information is used in a read-across approach in the assessment of the target substance. For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Type:
- log Pow
- Partition coefficient:
- ca. -0.54
- Temp.:
- 25 °C
- pH:
- 7
- Conclusions:
- A study was performed in accordance with EU method A.8 and OECD guideline 107 and in compliance with GLP. The Pow of the test substance was calculated to be 2.9E-01 (log Pow -0.54) using the Rekker calculation method.
- Executive summary:
Due to the poor UV-absorption ability of the test item an enzymatic reaction in combination with UV-detection was performed. However, no suitable method for the detection of lactic acid in n-octanol and/or water in the required concentration range could be developed (technically not feasible). Therefore, the partition coefficient of the test substance was calculated using the Rekker calculation method by the software PrologP 6.0, module in Pallas 3.0, CompuDrug International, San Francisco, CA, USA. The calculated log Pow is -0.54.
This information is used in a read-across approach in the assessment of the target substance. For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Endpoint:
- partition coefficient
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Justification for type of information:
- This information is used in a read-across approach in the assessment of the target substance. For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Reason / purpose for cross-reference:
- read-across source
- Type:
- log Pow
- Partition coefficient:
- ca. -0.65
- Temp.:
- 20 °C
- Remarks on result:
- other: QSAR calculation
- Conclusions:
- The log octanol-water partition coefficient of lactic acid, calculated by a QSAR method (KOWWin, EpiSuite), is -0.65.
- Executive summary:
The log octanol-water partition coefficient of lactic acid, calculated by a QSAR method (KOWWin, EpiSuite), is -0.65.
In support of this calculation, publicly available values for lactic acid are quoted in the expert statement:
European HPV programme: log Pow = -0.62
IPCS International program on Chemical Safety: log Pow = -0.6
This information is used in a read-across approach in the assessment of the target substance. For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Endpoint:
- partition coefficient
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Justification for type of information:
- This information is used in a read-across approach in the assessment of the target substance. For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
- Reason / purpose for cross-reference:
- read-across source
- Type:
- log Pow
- Partition coefficient:
- ca. -0.72
- Remarks on result:
- other: Experimental value by Leonard et al. (1948), included in the KOWWin reference data base, training data set.
- Type:
- log Pow
- Partition coefficient:
- ca. -0.65
- Remarks on result:
- other: KOWWin estimate - not reliable due to autocorrelation
- Details on results:
- Leonard et al. (1948) quote the partition coefficient (water/n-octanol) as 5.2, which is the reverse of the conventional n-octanol/water partition coefficient. Accordingly, the log Pow can calculated using the formula: log10(1/5.2) = -0.72.
- Conclusions:
- The log Kow of lactic acid was found to be -0.72.
- Executive summary:
Lactic acid is included in the KOWWin reference substance data base, training data set. The quoted figure of –0.72 is claimed to be an experimental value, originating from the publication by Leonard et al. (1948). Although the QSAR estimate generated by KOWWin of -0.65 matches the former values very well it cannot be used for reasons of autocorrelation. Therefore, the experimental value of -0.72 is favoured.
This information is used in a read-across approach in the assessment of the target substance. For details and justification of read-across please refer to the read-across report attached to IUCLID section 13.
Referenceopen allclose all
It was found that n-octanol influences the enzyme reaction and that the tested UV-Vis spectrophotometric method involving enzymatic reactions is not a suitable method to determine the test substance concentration in samples taken from the partition coefficient (shake flask method) at low concentration levels.
Since an analytical method for the determination of L(+)-lactic acid concentrations in samples from the shake flask method and/or estimation method could not be developed, these methods are not applicable for the determination of log Pow of the test substance.
The HPLC method is also not applicable as it covers log Pow values in the range of 0 to 6, and because the calculation method indicated a log Pow value outside this range. Based on this, it was decided to report the result of the calculation method.
Description of key information
All available evidence indicates that the octanol-water partition coefficient of lactic acid is significantly below 0. In a worst-case approach, and supported by weight of evidence from a range of published studies, the highest value of log Pow= -0.54 (QSAR estimate) is selected.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- -0.54
- at the temperature of:
- 20 °C
Additional information
In a weight-of-evidence approach the partition coefficient of D-(-)-lactic acid is assessed to range between -0.72 and -0.54. Typically the racemic mixture (lactic acid) is referred to, but since enantiomers are optical antipodes they do not differ in their physicochemical properties. Therefore, data on the lactic acid racemate can be used for D-(-)-lactic acid without restriction.
Early publications claim to have measured the concentrations of lactic acid in n-octanol and water, either by titration against phenol red (Leonard et al., 1948), or, in most other cases, by an unspecified method. This limits the individual reliability of the reported values. However, all reported partition coefficients are consistent, and are supported by a recent QSAR calculation using the software PrologP 6.0 (Selditz, 2014; log Pow= -0.54). Note that the QSAR estimate generated by KOWWin (EpiSuite) cannot be used since the experimental value by Leonard et al. (1948) is included in the training data set (autocorrelation).
In conclusion, adopting a worst-case approach (highest predicted distribution into biota, if any) the highest reported partition coefficient of log Pow= -0.54 is selected as the key value for chemical safety assessment. The weight of evidence from all other identified literature sources indicates that this value is fully appropriate for risk assessment.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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