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Diss Factsheets
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EC number: 907-672-2 | CAS number: -
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a (Q)SAR model, with limited documentation / justification, but validity of model and reliability of prediction considered adequate based on a generally acknowledged source
- Justification for type of information:
- QSAR prediction
- Qualifier:
- according to guideline
- Guideline:
- other: The Molecular connectivity index approach was used, as was described by Meylan et al; Environmental Science and Technology, 26, 1560 - 1567, 1992
- Principles of method if other than guideline:
- The molecular connectivity (MCI) approach is used to derive the appropriate Koc value. For non-polar compounds the QSAR has a simple linear form: log Koc = 0.5213 MCI + 0.60. For more polar compounds corrections are made for the polar groups.
- GLP compliance:
- no
- Type of method:
- other: QSAR
- Media:
- other: QSAR
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
not applicable - Radiolabelling:
- no
- Test temperature:
- The QSAR is applicable to ambient temperatures
- Details on study design: HPLC method:
- not applicable
- Analytical monitoring:
- not required
- Details on sampling:
- not applicable
- Details on matrix:
- not applicable
- Details on test conditions:
- not applicable
- Type:
- log Koc
- Value:
- 3.5
- Details on results (HPLC method):
- not applicable
- Adsorption and desorption constants:
- not applicable
- Recovery of test material:
- not applicable
- Concentration of test substance at end of adsorption equilibration period:
- not applicable
- Concentration of test substance at end of desorption equilibration period:
- not applicable
- Details on results (Batch equilibrium method):
- not applicable
- Statistics:
- not applicable
- Validity criteria fulfilled:
- yes
- Conclusions:
- With the MCI QSAR a log KOC of 3.50 was calculated.
- Executive summary:
EPI Suite v4.10 was used to calculate the log Koc value of BDPP. The QSAR is based on the well documented MCI model and the resulting log Koc equals 3.50.
For this property of the compound, the model has a well defined algorithm. The physical and chemical properties of BDPP fall well within the the molecular weight of the training and validation dataset. The training dataset consists of 447 compounds of which some have similar structures to DBPP. The plot of experimental log Koc against modelled Koc has an R2 of 0.90, a SD of 0.34 and an average deviation of 0.273. Therefore the calculated value of log Koc can be considered to be reliable.
- Endpoint:
- adsorption / desorption
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a (Q)SAR model, with limited documentation / justification, but validity of model and reliability of prediction considered adequate based on a generally acknowledged source
- Justification for type of information:
- QSAR prediction
- Qualifier:
- according to guideline
- Guideline:
- other: The Molecular connectivity index approach was used, as was described by Meylan et al; Environmental Science and Technology, 26, 1560 - 1567, 1992
- Principles of method if other than guideline:
- The molecular connectivity (MCI) approach is used to derive the appropriate Koc value. For non-polar compounds the QSAR has a simple linear form: log Koc = 0.5213 MCI + 0.60. For more polar compounds corrections are made for the polar groups.
- GLP compliance:
- no
- Type of method:
- other: QSAR
- Media:
- other: QSAR
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
not applicable - Radiolabelling:
- no
- Test temperature:
- The QSAR is applicable to ambient temperatures
- Details on study design: HPLC method:
- not applicable
- Analytical monitoring:
- not required
- Details on sampling:
- not applicable
- Details on matrix:
- not applicable
- Details on test conditions:
- not applicable
- Type:
- log Koc
- Value:
- 2.97
- Details on results (HPLC method):
- not applicable
- Adsorption and desorption constants:
- not applicable
- Recovery of test material:
- not applicable
- Concentration of test substance at end of adsorption equilibration period:
- not applicable
- Concentration of test substance at end of desorption equilibration period:
- not applicable
- Details on results (Batch equilibrium method):
- not applicable
- Statistics:
- not applicable
- Validity criteria fulfilled:
- yes
- Conclusions:
- With the MCI QSAR a log KOC of 2.97 was calculated.
- Executive summary:
EPI Suite v4.10 was used to calculate the log Koc value of DBPP. The QSAR is based on the well documented MCI model and the resulting log Koc equals 2.97.
For this well defined property of the compound, the model has a well defined algorithm. The physical and chemical properties of DBPP fall well within the the molecular weight of the training and validation dataset. The training dataset consists of 447 compounds of which some have similar structures to DBPP. The plot of experimental log Koc against modelled Koc has an R2 of 0.90, a SD of 0.34 and an average deviation of 0.273. Therefore the calculated value of log Koc can be considered to be reliable.
- Endpoint:
- adsorption / desorption
- Remarks:
- other: QSAR
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The study result is based on a QSAR, with a well documented model and the properties of the substance well within the applicability domain of the model.
- Justification for type of information:
- QSAR prediction
- Qualifier:
- according to guideline
- Guideline:
- other: The Molecular connectivity index approach was used, as was described by Meylan et al; Environmental Science and Technology, 26, 1560 - 1567, 1992
- Principles of method if other than guideline:
- The molecular connectivity (MCI) approach is used to derive the appropriate Koc value. For non-polar compounds the QSAR has a simple linear form: log Koc = 0.5213 MCI + 0.60. For more polar compounds corrections are made for the polar groups.
- GLP compliance:
- no
- Type of method:
- other: QSAR
- Media:
- other: QSAR
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
not applicable - Radiolabelling:
- no
- Test temperature:
- The QSAR is applicable to ambient temperatures
- Details on study design: HPLC method:
- not applicable
- Analytical monitoring:
- not required
- Details on sampling:
- not applicable
- Details on matrix:
- not applicable
- Details on test conditions:
- not applicable
- Type:
- log Koc
- Value:
- 3.37
- Details on results (HPLC method):
- not applicable
- Adsorption and desorption constants:
- not applicable
- Recovery of test material:
- not applicable
- Concentration of test substance at end of adsorption equilibration period:
- not applicable
- Concentration of test substance at end of desorption equilibration period:
- not applicable
- Details on results (Batch equilibrium method):
- not applicable
- Statistics:
- not applicable
- Validity criteria fulfilled:
- yes
- Conclusions:
- With the MCI QSAR a log KOC of 3.37 was calculated.
- Executive summary:
EPI Suite v4.10 was used to calculate the log Koc value of TBP. The QSAR is based on the well documented MCI model and the resulting log Koc equals 3.37.
For this property of the compound, the model has a well defined algorithm. The physical and chemical properties of TBP fall well within the the molecular weight of the training and validation dataset. The training dataset consists of 447 compounds of which some have similar structures to DBPP. The plot of experimental log Koc against modelled Koc has an R2 of 0.90, a SD of 0.34 and an average deviation of 0.273. Therefore the calculated value of log Koc can be considered to be reliable.
Referenceopen allclose all
The MCI model has a clear algorithm for this defined property of the compound. Currently there is no well defined model domain, however the modelling results will be less reliable if the molecular weight is not in the range of the molecular weights of the training and validation dataset. The molecular weight of BDPP falls well within the the molecular weight of the training and validation dataset.
The training dataset consists of 447 compounds of which some have similar structures to BDPP. The plot of experimental log Koc against modelled Koc has an R2 of 0.90, a SD of 0.34 and an average deviation of 0.273.
The MCI model has a clear algorithm for this property of the compound. Currently there is no well defined model domain, however the modelling results will be less reliable if the molecular weight is not in the range of the molecular weights of the training and validation dataset. The molecular weight of DBPP falls well within the the molecular weight of the training and validation dataset.
The training dataset consists of 447 compounds of which some have similar structures to DBPP. The plot of experimental log Koc against modelled Koc has an R2 of 0.90, a SD of 0.34 and an average deviation of 0.273.
The MCI model has a clear algorithm for this defined property of the compound. Currently there is no well defined model domain, however the modelling results will be less reliable if the molecular weight is not in the range of the molecular weights of the training and validation dataset. The molecular weight of TBP falls well within the the molecular weight of the training and validation dataset.
The training dataset consists of 447 compounds of which some have similar structures to TBP. The plot of experimental log Koc against modelled Koc has an R2 of 0.90, a SD of 0.34 and an average deviation of 0.273.
Description of key information
Two independent well documented QSARs were used to calculate the log Koc for DBPP. The results of the QSARs are very similar with a value of 2.97 obtained with the MCI approach and a value of 3.06 with an approach based on the log Kow value.
As the MCI QSAR is considered slightly more reliable and the lowest value is considered more critical in the environmental assessment (aquatic compartment) this value as the key value for the CSA.
Key value for chemical safety assessment
- Koc at 20 °C:
- 933
Additional information
Two independent QSARs were used to calculate the log Koc value of DiButyl Phenyl Phosphate (DBPP), Tri Butyl Phosphate (TBP) and Butyl DiPhenyl Phosphate (BDPP). The QSARs are well documented, have a clear regression model and are used for a well defined property for compounds that fall well within the applicability domain of the QSAR.
Compound log Koc MCI-QSAR log Koc Kow-QSAR
DBPP 2.97 3.06
TBP 3.37 3.24
BDPP 3.50 3.14
The different compounds have similar Koc values and the different QSAR results are also similar. As the MCI-QSAR is considered to be slightly more reliable this is the starting point for further calculations. The Koc values of the two other compounds do not give reason to deviate from the value obtained for DBPP.
[LogKoc: 2.97]
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