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EC number: 239-556-6 | CAS number: 15520-10-2
- 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:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 17 Nov - 14 Dec 1989
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study (EPA Guidelines 40 CFR 796.1550).
- Qualifier:
- according to guideline
- Guideline:
- other: EPA Guidelines 40 CFR 796.1550
- Principles of method if other than guideline:
- MPMD was partitioned between n-octanol and water at 25 °C and at pH values of 5.0, 7.0, and 9.0. The phases were separated and analysed for MPMD using gas chromatographic (GC) analysis.
- GLP compliance:
- yes
- Type of method:
- estimation method (solubility ratio)
- Partition coefficient type:
- octanol-water
- Analytical method:
- gas chromatography
- Type:
- Pow
- Partition coefficient:
- <= 7.9
- Temp.:
- 25 °C
- pH:
- 9
- Remarks on result:
- other: corrected for ionisation.
- Type:
- log Pow
- Partition coefficient:
- <= 1
- Temp.:
- 25 °C
- pH:
- 9
- Remarks on result:
- other: corrected for ionisation.
- Details on results:
- See below.
- Conclusions:
- The log Pow of the test substance is below 1 at pH 9 and 25 °C.
- Executive summary:
The partition coefficient was determined according to EPA Guidelines 40 CFR 796.1550.
The test substance MPMD was partitioned between n-octanol and water at 25 °C and at pH values of 5.0, 7.0, and 9.0. The phases were separated and analysed for MPMD using gas chromatographic (GC) analysis. Actually, no MPMD was found in the octanol phases. Therefore, the partition coefficient was calculated for pH=9 using the detection limit as worst-case-concentration of MPMD in n-octanol. The yielded partition coefficient value was then corrected for ionisation by calculation using literature data of the pka values.
The log Pow of the test substance is below 1 at pH 9 and 25 °C.
Reference
Chromatography
Under the conditions used in this study, MPMD eluted with a retention time of 0.7-0.9 minutes. Analytical precision was approximately 0.6% (standard error of the mean). Typical calibration curve R2 values were >0.995. The detection limit was <0.01 mM.
Partitioning
Under the conditions employed in this study, MPMD partitioned exclusively into the aqueous phase. Concentrations in the aqueous phase after equilibration were approximately 2.0 mM (high concentration) and 0.20 mM (low concentration). The total recovery of MPMD (for replicate determinations) ranged from 79 to 119% nominal (high concentration) and 90 to 120% nominal (low concentration).
Kow Estimation
Since MPMD could not be detected in the n-octanol phase at either the initial test concentrations or at any pH, a Kow value was calculated assuming the concentration in the n-octanol phase was equal to the detection limit (worst-case situation). Using pKa values for MPMD of 10.0 and 11.2 from literature (Reference 1: Conoco Analytical Report # 711539, 1987), the n-octanol/water partition coefficient of MPMD at pH 9.0 was corrected for ionisation.
Uncorrected:
Kow =/< (0.01 mM/2.0 mM)
Kow =/< 0.005
Corrected:
Kow (corr) = Kow * exp ((pKa1 - pH) + (pKa2 - pH)
Kow (corr) =/< 7.9
Due to the detection limits of this partitioning study, Kow values were not calculated at the other pH values or at the lower concentration. Partitioning of MPMD into the n-octanol phase would theoretically be 100 and 10000 times less at pH values of 7.0 and 5.0, respectively.
Description of key information
The log Pow of the test substance is below 1 at pH 9 and 25 °C.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 1
- at the temperature of:
- 25 °C
Additional information
The partition coefficient was determined according to EPA Guidelines 40 CFR 796.1550.
The test substance MPMD was partitioned between n-octanol and water at 25 °C and at pH values of 5.0, 7.0, and 9.0. The phases were separated and analysed for MPMD using gas chromatographic (GC) analysis. Actually, no MPMD was found in the octanol phases. Therefore, the partition coefficient was calculated for pH=9 using the detection limit as worst-case-concentration of MPMD in n-octanol. The yielded partition coefficient value was then corrected for ionisation by calculation using literature data of the pka values.
The log Pow of the test substance is below 1 at pH 9 and 25 °C.
A conservative log Pow value of 1 is taken for safety assessment purposes.
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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