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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
Hydrolysis
Administrative data
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The QSAR is well documented the test compound fits well within applicability domain and the QSAR is applied for a well defined endpoint
- Justification for type of information:
- QSAR prediction
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- other: T. Mill, W. Haag, P. Penwell, T. Pettit and H. Johnson. Environmental fate and exposure studies development of a PC-SAR for hydrolysis: Esters, alkyl halides and epoxides. EPA contract 68-02-4254. SRI International, 1987
- Principles of method if other than guideline:
- The chemical structure of the compound is the starting point of the analysis. A specific approach was developed for different groups of compounds.For phosphate esters like DBPP a specific QSAR was available.
Hydrolysis rates were based on which chemical bonds are present in the compound and estmates of parameters to describe the steric hindrance for each substituent in the phosphate ester. - GLP compliance:
- no
- Specific details on test material used for the study:
- not applicable
- Analytical monitoring:
- not required
- Details on sampling:
- not applicable
- Buffers:
- not applicable
- Estimation method (if used):
- The estimation method is based on T. Mill, W. Haag, P. Penwell, T. Pettit and H. Johnson. Environmental fate and exposure studies development of a PC-SAR for hydrolysis: Esters, alkyl halides and epoxides. EPA contract 68-02-4254. SRI International, 1987. This method was adapted to make predictions on phosphate esters, described by W.M. Meylan and P.H. Howard, Environmental Science Centre, Syracuse Research Corporation, Syracuse, NY 13212, 2007
- Details on test conditions:
- not applicable
- Number of replicates:
- not applicable
- Statistical methods:
- not appliacble
- Transformation products:
- not specified
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 19.25 yr
- pH:
- 10
- Temp.:
- 25 °C
- DT50:
- 7.79 d
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The hydrolysis half life of BDPP was estimated for a pH of 5 to 10. Currently it is not possible to derive an acid based hydrolysis rate. The estimated half life of BDPP at ambient temperatures and pH = 5 is 180 years The estimated half life of BDPP at ambient temperatures and pH = 6 is 102.3 years The estimated half life of BDPP at ambient temperatures and pH = 7 is 19.25 years The estimated half life of BDPP at ambient temperatures and pH = 8 is 21.4 years The estimated half life of BDPP at ambient temperatures and pH = 9 is 77.82 days The estimated half life of BDPP at ambient temperatures and pH = 10 is 7.79 days
- Executive summary:
The half life for hydrolysis of BDPP was estimated using a QSAR. This QSAR is well defined and BDPP falls well within the applicability domain of the QSAR.
The hydrolysis half life of BDPP was estimated for different pHs. Currently it is not possible to derive an acid based hydrolysis rate. The estimated half life of BDPP at ambient temperatures and pH = 7 is 19.25 years The estimated half life of DBPP at ambient temperatures is minimal at a pH of 10 (7.79 days).
Based on this information it can be concluded that BDPP has a low to non-existing potential for hydrolysis around neutral pH. At higher pH values some potential for hydrolysis exists.
- Endpoint:
- hydrolysis
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The QSAR is well documented the test compound fits well within applicability domain and the QSAR is applied for a well defined endpoint
- Justification for type of information:
- QSAR prediction
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- other: T. Mill, W. Haag, P. Penwell, T. Pettit and H. Johnson. Environmental fate and exposure studies development of a PC-SAR for hydrolysis: Esters, alkyl halides and epoxides. EPA contract 68-02-4254. SRI International, 1987
- Principles of method if other than guideline:
- The chemical structure of the compound is the starting point of the analysis. A specific approach was developed for different groups of compounds.For phosphate esters like DBPP a specific QSAR was available.
Hydrolysis rates were based on which chemical bonds are present in the compound and estmates of parameters to describe the steric hindrance for each substituent in the phosphate ester. - GLP compliance:
- no
- Specific details on test material used for the study:
- not applicable
- Analytical monitoring:
- not required
- Details on sampling:
- not applicable
- Buffers:
- not applicable
- Estimation method (if used):
- The estimation method is based on T. Mill, W. Haag, P. Penwell, T. Pettit and H. Johnson. Environmental fate and exposure studies development of a PC-SAR for hydrolysis: Esters, alkyl halides and epoxides. EPA contract 68-02-4254. SRI International, 1987. This method was adapted to make predictions on phosphate esters, described by W.M. Meylan and P.H. Howard, Environmental Science Centre, Syracuse Research Corporation, Syracuse, NY 13212, 2007
- Details on test conditions:
- not applicable
- Number of replicates:
- not applicable
- Statistical methods:
- not appliacble
- Transformation products:
- not specified
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 42.3 yr
- pH:
- 10
- Temp.:
- 25 °C
- DT50:
- 140.4 d
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The hydrolysis half life of DBPP was estimated for a pH of 5 to 10. Currently it is not possible to derive an acid based hydrolysis rate. The estimated half life of DBPP at ambient temperatures and pH = 5 is 47.4 years The estimated half life of DBPP at ambient temperatures and pH = 6 is 46.9 years The estimated half life of DBPP at ambient temperatures and pH = 7 is 42.3 years The estimated half life of DBPP at ambient temperatures and pH = 8 is 21.4 years The estimated half life of DBPP at ambient temperatures and pH = 9 is 3.6 years The estimated half life of DBPP at ambient temperatures and pH = 10 is 140.4 days
- Executive summary:
The half life for hydrolysis of DBPP was estimated using a QSAR. This QSAR is well defined and DBPP falls well within the applicability domain of the QSAR.
The hydrolysis half life of DBPP was estimated for different pHs. Currently it is not possible to derive an acid based hydrolysis rate. The estimated half life of DBPP at ambient temperatures and pH = 7 is 42.3 years The estimated half life of DBPP at ambient temperatures is minimal at a pH of 10 (140.4 days).
Based on this information it can be concluded that DBPP has a low to non-existing potential for hydrolysis.
- Endpoint:
- hydrolysis
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The QSAR is well documented the test compound fits well within applicability domain and the QSAR is applied for a well defined endpoint
- Justification for type of information:
- QSAR prediction
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- other: T. Mill, W. Haag, P. Penwell, T. Pettit and H. Johnson. Environmental fate and exposure studies development of a PC-SAR for hydrolysis: Esters, alkyl halides and epoxides. EPA contract 68-02-4254. SRI International, 1987
- Principles of method if other than guideline:
- The chemical structure of the compound is the starting point of the analysis. A specific approach was developed for different groups of compounds.For phosphate esters like TBP a specific QSAR was available.
Hydrolysis rates were based on which chemical bonds are present in the compound and estmates of parameters to describe the steric hindrance for each substituent in the phosphate ester. - GLP compliance:
- no
- Specific details on test material used for the study:
- not applicable
- Analytical monitoring:
- not required
- Details on sampling:
- not applicable
- Buffers:
- not applicable
- Estimation method (if used):
- The estimation method is based on T. Mill, W. Haag, P. Penwell, T. Pettit and H. Johnson. Environmental fate and exposure studies development of a PC-SAR for hydrolysis: Esters, alkyl halides and epoxides. EPA contract 68-02-4254. SRI International, 1987. This method was adapted to make predictions on phosphate esters, described by W.M. Meylan and P.H. Howard, Environmental Science Centre, Syracuse Research Corporation, Syracuse, NY 13212, 2007
- Details on test conditions:
- not applicable
- Number of replicates:
- not applicable
- Statistical methods:
- not appliacble
- Transformation products:
- not specified
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 11.45 yr
- pH:
- 10
- Temp.:
- 25 °C
- DT50:
- 4.37 yr
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The hydrolysis half life of TBP was estimated for a pH of 5 to 10. Currently it is not possible to derive an acid based hydrolysis rate. The estimated half life of TBP at ambient temperatures and pH = 5 is 11.47 years The estimated half life of TBP at ambient temperatures and pH = 6 is 11.47 years The estimated half life of TBP at ambient temperatures and pH = 7 is 11.45 years The estimated half life of TBP at ambient temperatures and pH = 8 is 11.29 years The estimated half life of TBP at ambient temperatures and pH = 9 is 9.87 years The estimated half life of TBP at ambient temperatures and pH = 10 is 4.37 years
- Executive summary:
The half life for hydrolysis of TBP was estimated using a QSAR. This QSAR is well defined and TBP falls well within the applicability domain of the QSAR.
The hydrolysis half life of TBP was estimated for different pHs. Currently it is not possible to derive an acid based hydrolysis rate. The estimated half life of TBP at ambient temperatures and pH = 7 is 11.45 years The estimated half life of TBP at ambient temperatures is minimal at a pH of 10 (4.37 years).
Based on this information it can be concluded that TBP has a low to non-existing potential for hydrolysis.
Referenceopen allclose all
Description of key information
The hydrolysis half life of the constituents of the DBPP multi-constituent were estimated for different pHs using a QSAR (EpiSuite v4.10). This QSAR is well defined and the DBPP constituents falls well within the applicability domain of the QSAR. The estimated half life of DBPP mono-constituent is regarded the most relevant one, the results of the other constituents are in the same range (>100 days to years). At ambient temperatures and pH = 7 the hydrolysis half life is 42.3 years for the DBPP mono-constituent. The estimated half life of DBPP mono-constituent at ambient temperatures and pH = 10 is 140.4 days. In conclusion it can be stated that the substance has a low to non-existing hydrolysis potential.
Key value for chemical safety assessment
- Half-life for hydrolysis:
- 42.3 yr
- at the temperature of:
- 25 °C
Additional information
The hydrolysis half life of Dibutyl phenyl phosphate (DBPP), Tributyl phosphate (TBP) and Butyl diphenyl phosphate (BDPP) was estimated for different pHs using a QSAR (EpiSuite v4.10). This QSAR is well defined and all three phosphate esters fall well within the applicability domain of the QSAR.
Compound pH Hydrolysis half life
DBPP 7 42.31 years
DBPP 10 140.4 days
TBP 7 11.45 years
TBP 10 4.37 years
BDPP 7 19.25 years
BDPP 10 7.79 days
The estimated half life of all three compounds at ambient temperatures and pH = 7 is well over 10 years. In conclusion it can be stated that all three substances have a low to non-existing hydrolysis potential at neutral pHs.
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