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EC number: 269-134-7 | CAS number: 68187-91-7
- 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
Phototransformation in air
Administrative data
Link to relevant study record(s)
- Endpoint:
- phototransformation in air
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2013
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
: EPI Suite, by the U.S. Envirnmental Protection Agency
2. MODEL (incl. version number): AOPWIN v1.92
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL : HN(H)(H)OS(=O)(=O)OC(CCCCCCCC(=O)OCC(COC(=O)CCCCCCCC=CCCCCCCCC)OC(=O)CCCCCCCC=CCCCCCCCC)CCCCCCCCC
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL : The model is included in the EPI Suite to which the OECD QSAR toolbox makes reference.
5. APPLICABILITY DOMAIN : The estimation methods used by AOPWIN are based upon the structure-activity relationship (SAR) methods developed by Dr. Roger Atkinson and co-workers, as referred in the On-Line User's Guide of the model. Syracuse Research Corporation has derived some additional fragment and reaction values from more recent experimental data. Appendix I of the On-Line User's Guide lists all fragment and reaction values used by AOPWIN. The complete training sets for AOPWIN's estimation methodology are not available. Therefore, describing a precise estimation domain for this methodology is not possible. Anyway, the fragments included in the molecule are present in compounds considered in the model.
6. ADEQUACY OF THE RESULT: The prediction is considered adequate for the purpose of the risk assessment as a weight-of evidence result, as the model is considered reliable and the molecule fragments are present in compounds considered in the model. - Guideline:
- other: ECHA Guidance on information requirements and chemical safety assessment - Chapter R.06: QSARs and grouping of chemicals - May 2008
- Principles of method if other than guideline:
- The Atmospheric Oxidation Program for Microsoft Windows (AOPWIN) estimates the rate constant for the atmospheric, gas-phase reaction between photochemically produced hydroxyl radicals and organic chemicals. It also estimates the rate constant for the gas-phase reaction between ozone and olefinic/acetylenic compounds. The rate constants estimated by the program are then used to calculate atmospheric half-lives for organic compounds based upon average atmospheric concentrations of hydroxyl radicals and ozone.
The estimation methods used by AOPWIN are based upon the structure-activity relationship (SAR) methods developed by Dr. Roger Atkinson and co-workers (Atkinson, 1985, 1986, 1987, 1991; Atkinson and Carter, 1984; Biermann et al, 1985; Kwok et al, 1992, Kwok and Atkinson, 1995; Kwok et al, 1996).
AOPWIN incorporates updated fragment and reaction values as cited in Kwok and Atkinson (1995). In addition, Syracuse Research Corporation has derived some additional fragment and reaction values from new experimental data. A journal article that discusses the Atmospheric Oxidation Program has been published (Meylan and Howard, 1993).
AOPWIN requires only a chemical structure to make these predictions. - GLP compliance:
- no
- Specific details on test material used for the study:
- SMILES notation: HN(H)(H)OS(=O)(=O)OC(CCC=CCC=CCC=CCC=CCC=CCCC(=O)OCC(COC(=O)CCCCCCCC=CCCCCCCCCCC)OC(=O)CCCC=CCC=CCC=CCC=CCC=CCC)CC
- DT50:
- ca. 0.25 h
- Test condition:
- OH concentration: 1.5E+06 OH radicals/cm3; Half-life: 12 h/day
- Conclusions:
- In the atmosphere a representative molecule of the sulfated oils (oils, fish, sulfated, ammonium salt) is degraded by reaction with photochemically-produced hydroxyl radicals with a half-life of approximately 0.25 hours.
- Executive summary:
The stability of a representative molecule of the sulfated oils (oils, fish, sulfated, ammonium salt) in the atmosphere was estimated using the software AOPWIN (v 1.92). It is predicted that the molecule will be degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals. The half-life for this reaction in air is estimated to be approximately 0.25 hours.
- Endpoint:
- phototransformation in air
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2013
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
: EPI Suite, by the U.S. Envirnmental Protection Agency
2. MODEL (incl. version number): AOPWIN v1.92
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL : HN(H)(H)OS(=O)(=O)OC(CCCCCCCC(=O)OCC(COC(=O)CCCCCCCC=CCCCCCCCC)OC(=O)CCCCCCCC=CCCCCCCCC)CCCCCCCCC
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL : The model is included in the EPI Suite to which the OECD QSAR toolbox makes reference.
5. APPLICABILITY DOMAIN : The estimation methods used by AOPWIN are based upon the structure-activity relationship (SAR) methods developed by Dr. Roger Atkinson and co-workers, as referred in the On-Line User's Guide of the model. Syracuse Research Corporation has derived some additional fragment and reaction values from more recent experimental data. Appendix I of the On-Line User's Guide lists all fragment and reaction values used by AOPWIN. The complete training sets for AOPWIN's estimation methodology are not available. Therefore, describing a precise estimation domain for this methodology is not possible. Anyway, the fragments included in the molecule are present in compounds considered in the model.
6. ADEQUACY OF THE RESULT: The prediction is considered adequate for the purpose of the risk assessment as a weight-of evidence result, as the model is considered reliable and the molecule fragments are present in compounds considered in the model. - Guideline:
- other: ECHA Guidance on information requirements and chemical safety assessment - Chapter R.06: QSARs and grouping of chemicals - May 2008
- Principles of method if other than guideline:
- The Atmospheric Oxidation Program for Microsoft Windows (AOPWIN) estimates the rate constant for the atmospheric, gas-phase reaction between photochemically produced hydroxyl radicals and organic chemicals. It also estimates the rate constant for the gas-phase reaction between ozone and olefinic/acetylenic compounds. The rate constants estimated by the program are then used to calculate atmospheric half-lives for organic compounds based upon average atmospheric concentrations of hydroxyl radicals and ozone.
The estimation methods used by AOPWIN are based upon the structure-activity relationship (SAR) methods developed by Dr. Roger Atkinson and co-workers (Atkinson, 1985, 1986, 1987, 1991; Atkinson and Carter, 1984; Biermann et al, 1985; Kwok et al, 1992, Kwok and Atkinson, 1995; Kwok et al, 1996).
AOPWIN incorporates updated fragment and reaction values as cited in Kwok and Atkinson (1995). In addition, Syracuse Research Corporation has derived some additional fragment and reaction values from new experimental data. A journal article that discusses the Atmospheric Oxidation Program has been published (Meylan and Howard, 1993).
AOPWIN requires only a chemical structure to make these predictions. - GLP compliance:
- no
- Specific details on test material used for the study:
- SMILES notation: O=C(CCC=CCC=CCC=CCC=CCC=CCCC(CC)OS(=O)(=O)O[Na])OCC(COC(=O)CCCCCCCC=CCCCCCCCCCC)OC(=O)CCCC=CCC=CCC=CCC=CCC=CCC
- DT50:
- ca. 0.25 h
- Test condition:
- OH concentration: 1.5E+06 OH radicals/cm3; Half-life: 12 h/day
- Conclusions:
- In the atmosphere a representative molecule of the sulfated oils (oils, fish, sulfated, ammonium salts) is degraded by reaction with photochemically-produced hydroxyl radicals with a half-life of approximately 0.25 hours.
- Executive summary:
The stability of a representative molecule of the sulfated oils in the atmosphere was estimated using the software AOPWIN (v 1.92). It is predicted that the molecule will be degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals. The half-life for this reaction in air is estimated to be approximately 0.25 hours.
- Endpoint:
- phototransformation in air
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2013
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
: EPI Suite, by the U.S. Envirnmental Protection Agency
2. MODEL (incl. version number): AOPWIN v1.92
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL : HN(H)(H)OS(=O)(=O)OC(CCCCCCCC(=O)OCC(COC(=O)CCCCCCCC=CCCCCCCCC)OC(=O)CCCCCCCC=CCCCCCCCC)CCCCCCCCC
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL : The model is included in the EPI Suite to which the OECD QSAR toolbox makes reference.
5. APPLICABILITY DOMAIN : The estimation methods used by AOPWIN are based upon the structure-activity relationship (SAR) methods developed by Dr. Roger Atkinson and co-workers, as referred in the On-Line User's Guide of the model. Syracuse Research Corporation has derived some additional fragment and reaction values from more recent experimental data. Appendix I of the On-Line User's Guide lists all fragment and reaction values used by AOPWIN. The complete training sets for AOPWIN's estimation methodology are not available. Therefore, describing a precise estimation domain for this methodology is not possible. Anyway, the fragments included in the molecule are present in compounds considered in the model.
6. ADEQUACY OF THE RESULT: The prediction is considered adequate for the purpose of the risk assessment as a weight-of evidence result, as the model is considered reliable and the molecule fragments are present in compounds considered in the model. - Guideline:
- other: ECHA Guidance on information requirements and chemical safety assessment - Chapter R.06: QSARs and grouping of chemicals - May 2008
- Principles of method if other than guideline:
- The Atmospheric Oxidation Program for Microsoft Windows (AOPWIN) estimates the rate constant for the atmospheric, gas-phase reaction between photochemically produced hydroxyl radicals and organic chemicals. It also estimates the rate constant for the gas-phase reaction between ozone and olefinic/acetylenic compounds. The rate constants estimated by the program are then used to calculate atmospheric half-lives for organic compounds based upon average atmospheric concentrations of hydroxyl radicals and ozone.
The estimation methods used by AOPWIN are based upon the structure-activity relationship (SAR) methods developed by Dr. Roger Atkinson and co-workers (Atkinson, 1985, 1986, 1987, 1991; Atkinson and Carter, 1984; Biermann et al, 1985; Kwok et al, 1992, Kwok and Atkinson, 1995; Kwok et al, 1996).
AOPWIN incorporates updated fragment and reaction values as cited in Kwok and Atkinson (1995). In addition, Syracuse Research Corporation has derived some additional fragment and reaction values from new experimental data. A journal article that discusses the Atmospheric Oxidation Program has been published (Meylan and Howard, 1993).
AOPWIN requires only a chemical structure to make these predictions. - GLP compliance:
- no
- Specific details on test material used for the study:
- SMILES notation: HN(H)(H)OS(=O)(=O)OC(CCCCCCCC(=O)OCC(COC(=O)CCCCCCCC=CCCCCCCCC)OC(=O)CCCCCCCC=CCCCCCCCC)CCCCCCCCC
- DT50:
- ca. 0.7 h
- Test condition:
- OH concentration: 1.5E+06 OH radicals/cm3; Half-life: 12 h/day
- Conclusions:
- In the atmosphere the representative molecule of the substance is degraded by reaction with photochemically-produced hydroxyl radicals with a half-life of approximately 0.7 hours.
- Executive summary:
The stability of the representative molecule of the substance in the atmosphere was estimated using the software AOPWIN (v 1.92). It is predicted that the substance will be degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals. The half-life for this reaction in air is estimated to be approximately 0.7 hours.
- Endpoint:
- phototransformation in air
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2013
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
: EPI Suite, by the U.S. Envirnmental Protection Agency
2. MODEL (incl. version number): AOPWIN v1.92
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL : HN(H)(H)OS(=O)(=O)OC(CCCCCCCC(=O)OCC(COC(=O)CCCCCCCC=CCCCCCCCC)OC(=O)CCCCCCCC=CCCCCCCCC)CCCCCCCCC
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL : The model is included in the EPI Suite to which the OECD QSAR toolbox makes reference.
5. APPLICABILITY DOMAIN : The estimation methods used by AOPWIN are based upon the structure-activity relationship (SAR) methods developed by Dr. Roger Atkinson and co-workers, as referred in the On-Line User's Guide of the model. Syracuse Research Corporation has derived some additional fragment and reaction values from more recent experimental data. Appendix I of the On-Line User's Guide lists all fragment and reaction values used by AOPWIN. The complete training sets for AOPWIN's estimation methodology are not available. Therefore, describing a precise estimation domain for this methodology is not possible. Anyway, the fragments included in the molecule are present in compounds considered in the model.
6. ADEQUACY OF THE RESULT: The prediction is considered adequate for the purpose of the risk assessment as a weight-of evidence result, as the model is considered reliable and the molecule fragments are present in compounds considered in the model. - Guideline:
- other: ECHA Guidance on information requirements and chemical safety assessment - Chapter R.06: QSARs and grouping of chemicals - May 2008
- Principles of method if other than guideline:
- The Atmospheric Oxidation Program for Microsoft Windows (AOPWIN) estimates the rate constant for the atmospheric, gas-phase reaction between photochemically produced hydroxyl radicals and organic chemicals. It also estimates the rate constant for the gas-phase reaction between ozone and olefinic/acetylenic compounds. The rate constants estimated by the program are then used to calculate atmospheric half-lives for organic compounds based upon average atmospheric concentrations of hydroxyl radicals and ozone.
The estimation methods used by AOPWIN are based upon the structure-activity relationship (SAR) methods developed by Dr. Roger Atkinson and co-workers (Atkinson, 1985, 1986, 1987, 1991; Atkinson and Carter, 1984; Biermann et al, 1985; Kwok et al, 1992, Kwok and Atkinson, 1995; Kwok et al, 1996).
AOPWIN incorporates updated fragment and reaction values as cited in Kwok and Atkinson (1995). In addition, Syracuse Research Corporation has derived some additional fragment and reaction values from new experimental data. A journal article that discusses the Atmospheric Oxidation Program has been published (Meylan and Howard, 1993).
AOPWIN requires only a chemical structure to make these predictions. - GLP compliance:
- no
- Specific details on test material used for the study:
- SMILES notation: O=C(CCCCCCCC=CCCCCCCCC)OC(COC(=O)CCCCCCCC=CCCCCCCCC)COC(=O)CCCCCCCC(CCCCCCCCC)OS(=O)(=O)O[Na]
- DT50:
- ca. 0.7 h
- Test condition:
- OH concentration: 1.5E+06 OH radicals/cm3; Half-life: 12 h/day
- Conclusions:
- In the atmosphere a representative molecule of the sulfated oils (Oils, vegetable, sulfated, sodium salts) is degraded by reaction with photochemically-produced hydroxyl radicals with a half-life of approximately 0.7 hours.
- Executive summary:
The stability of a representative molecule of the sulfated oils (Oils, vegetable, sulfated, sodium salts) in the atmosphere was estimated using the software AOPWIN (v 1.92). It is predicted that the substance will be degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals. The half-life for this reaction in air is estimated to be approximately 0.7 hours.
- Endpoint:
- phototransformation in air
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2013
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
: EPI Suite, by the U.S. Envirnmental Protection Agency
2. MODEL (incl. version number): AOPWIN v1.92
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL : HN(H)(H)OS(=O)(=O)OC(CCCCCCCC(=O)OCC(COC(=O)CCCCCCCC=CCCCCCCCC)OC(=O)CCCCCCCC=CCCCCCCCC)CCCCCCCCC
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL : The model is included in the EPI Suite to which the OECD QSAR toolbox makes reference.
5. APPLICABILITY DOMAIN : The estimation methods used by AOPWIN are based upon the structure-activity relationship (SAR) methods developed by Dr. Roger Atkinson and co-workers, as referred in the On-Line User's Guide of the model. Syracuse Research Corporation has derived some additional fragment and reaction values from more recent experimental data. Appendix I of the On-Line User's Guide lists all fragment and reaction values used by AOPWIN. The complete training sets for AOPWIN's estimation methodology are not available. Therefore, describing a precise estimation domain for this methodology is not possible. Anyway, the fragments included in the molecule are present in compounds considered in the model.
6. ADEQUACY OF THE RESULT: The prediction is considered adequate for the purpose of the risk assessment as a weight-of evidence result, as the model is considered reliable and the molecule fragments are present in compounds considered in the model. - Guideline:
- other: ECHA Guidance on information requirements and chemical safety assessment - Chapter R.06: QSARs and grouping of chemicals - May 2008
- Principles of method if other than guideline:
- The Atmospheric Oxidation Program for Microsoft Windows (AOPWIN) estimates the rate constant for the atmospheric, gas-phase reaction between photochemically produced hydroxyl radicals and organic chemicals. It also estimates the rate constant for the gas-phase reaction between ozone and olefinic/acetylenic compounds. The rate constants estimated by the program are then used to calculate atmospheric half-lives for organic compounds based upon average atmospheric concentrations of hydroxyl radicals and ozone.
The estimation methods used by AOPWIN are based upon the structure-activity relationship (SAR) methods developed by Dr. Roger Atkinson and co-workers (Atkinson, 1985, 1986, 1987, 1991; Atkinson and Carter, 1984; Biermann et al, 1985; Kwok et al, 1992, Kwok and Atkinson, 1995; Kwok et al, 1996).
AOPWIN incorporates updated fragment and reaction values as cited in Kwok and Atkinson (1995). In addition, Syracuse Research Corporation has derived some additional fragment and reaction values from new experimental data. A journal article that discusses the Atmospheric Oxidation Program has been published (Meylan and Howard, 1993).
AOPWIN requires only a chemical structure to make these predictions. - GLP compliance:
- no
- Specific details on test material used for the study:
- SMILES notation: HN(H)(H)OS(=O)(=O)OC(CC=CCCCCCCCC(=O)OCC(COC(=O)CCCCCCCC=CCC(O)CCCCCC)OC(=O)CCCCCCCC=CCC(O)CCCCCC)CCCCCC
- DT50:
- ca. 0.5 h
- Test condition:
- OH concentration: 1.5E+06 OH radicals/cm3; Half-life: 12 h/day
- Conclusions:
- In the atmosphere a representative molecule of the sulfated oils (castor oil, sulfated, ammonium salt) is degraded by reaction with photochemically-produced hydroxyl radicals with a half-life of approximately 0.5 hours.
- Executive summary:
The stability of a representative molecule of the sulfated oils (castor oil, sulfated, ammonium salt) in the atmosphere was estimated using the software AOPWIN (v 1.92). It is predicted that the molecule will be degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals. The half-life for this reaction in air is estimated to be approximately 0.5 hours.
- Endpoint:
- phototransformation in air
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2013
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
: EPI Suite, by the U.S. Envirnmental Protection Agency
2. MODEL (incl. version number): AOPWIN v1.92
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL : HN(H)(H)OS(=O)(=O)OC(CCCCCCCC(=O)OCC(COC(=O)CCCCCCCC=CCCCCCCCC)OC(=O)CCCCCCCC=CCCCCCCCC)CCCCCCCCC
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL : The model is included in the EPI Suite to which the OECD QSAR toolbox makes reference.
5. APPLICABILITY DOMAIN : The estimation methods used by AOPWIN are based upon the structure-activity relationship (SAR) methods developed by Dr. Roger Atkinson and co-workers, as referred in the On-Line User's Guide of the model. Syracuse Research Corporation has derived some additional fragment and reaction values from more recent experimental data. Appendix I of the On-Line User's Guide lists all fragment and reaction values used by AOPWIN. The complete training sets for AOPWIN's estimation methodology are not available. Therefore, describing a precise estimation domain for this methodology is not possible. Anyway, the fragments included in the molecule are present in compounds considered in the model.
6. ADEQUACY OF THE RESULT: The prediction is considered adequate for the purpose of the risk assessment as a weight-of evidence result, as the model is considered reliable and the molecule fragments are present in compounds considered in the model. - Guideline:
- other: ECHA Guidance on information requirements and chemical safety assessment - Chapter R.06: QSARs and grouping of chemicals - May 2008
- Principles of method if other than guideline:
- The Atmospheric Oxidation Program for Microsoft Windows (AOPWIN) estimates the rate constant for the atmospheric, gas-phase reaction between photochemically produced hydroxyl radicals and organic chemicals. It also estimates the rate constant for the gas-phase reaction between ozone and olefinic/acetylenic compounds. The rate constants estimated by the program are then used to calculate atmospheric half-lives for organic compounds based upon average atmospheric concentrations of hydroxyl radicals and ozone.
The estimation methods used by AOPWIN are based upon the structure-activity relationship (SAR) methods developed by Dr. Roger Atkinson and co-workers (Atkinson, 1985, 1986, 1987, 1991; Atkinson and Carter, 1984; Biermann et al, 1985; Kwok et al, 1992, Kwok and Atkinson, 1995; Kwok et al, 1996).
AOPWIN incorporates updated fragment and reaction values as cited in Kwok and Atkinson (1995). In addition, Syracuse Research Corporation has derived some additional fragment and reaction values from new experimental data. A journal article that discusses the Atmospheric Oxidation Program has been published (Meylan and Howard, 1993).
AOPWIN requires only a chemical structure to make these predictions. - GLP compliance:
- no
- Specific details on test material used for the study:
- SMILES notation: C(=O)(CCCCCCCC=CCC(CCCCCC)OS(=O)(=O)O[Na])OCC(COC(=O)CCCCCCCC=CCC(O)CCCCCC)OC(=O)CCCCCCCC=CCC(O)CCCCCC
- DT50:
- ca. 0.5 h
- Test condition:
- OH concentration: 1.5E+06 OH radicals/cm3; Half-life: 12 h/day
- Conclusions:
- In the atmosphere a representative molecule of the sulfated oils (castor oil, sulfated, sodium salt) is degraded by reaction with photochemically-produced hydroxyl radicals with a half-life of approximately 0.5 hours.
- Executive summary:
The stability of a representative molecule of the sulfated oils (castor oil, sulfated, sodium salt) in the atmosphere was estimated using the software AOPWIN (v 1.92). It is predicted that the molecule will be degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals. The half-life for this reaction in air is estimated to be approximately 0.5 hours.
Referenceopen allclose all
SMILES : HN(H)(H)OS(=O)(=O)OC(CCC=CCC=CCC=CCC=CCC=CCCC(=O)OCC(COC(=O)CCCCCCCC=
CCCCCCCCCCC)OC(=O)CCCC=CCC=CCC=CCC=CCC=CCC)CC
CHEM : Oils, fish, sulfated, ammonium salt
MOL FOR: C65 H106 N1 O10 S1
MOL WT : 1093.63
------------------- SUMMARY (AOP v1.92): HYDROXYL RADICALS (25 deg C) --------
Hydrogen Abstraction = 48.2274 E-12 cm3/molecule-sec
**Reaction with N, S and -OH = 0.0000 E-12 cm3/molecule-sec
Addition to Triple Bonds = 0.0000 E-12 cm3/molecule-sec
Addition to Olefinic Bonds = 507.6000 E-12 cm3/molecule-sec [Cis-isomer]
Addition to Olefinic Bonds = 576.0000 E-12 cm3/molecule-sec [Trans-isomer]
Addition to Aromatic Rings = 0.0000 E-12 cm3/molecule-sec
Addition to Fused Rings = 0.0000 E-12 cm3/molecule-sec
OVERALL OH Rate Constant = 555.8274 E-12 cm3/molecule-sec [Cis-isomer]
OVERALL OH Rate Constant = 624.2274 E-12 cm3/molecule-sec [Trans-isomer]
HALF-LIFE = 13.855 Min (12-hr day; 1.5E6 OH/cm3) [Cis-isomer]
HALF-LIFE = 12.337 Min (12-hr day; 1.5E6 OH/cm3) [Trans-isomer]
........................ ** Designates Estimation(s) Using ASSUMED Value(s)
------------------- SUMMARY (AOP v1.91): OZONE REACTION (25 deg C) -----------
OVERALL OZONE Rate Constant = 117.000000 E-17 cm3/molecule-sec [Cis-]
OVERALL OZONE Rate Constant = 180.000000 E-17 cm3/molecule-sec [Trans-]
HALF-LIFE = 14.105 Min (at 7E11 mol/cm3) [Cis-isomer]
HALF-LIFE = 9.168 Min (at 7E11 mol/cm3) [Trans-isomer]
NOTE: Reaction with Nitrate Radicals May Be Important!
Experimental Database: NO Structure Matches
SMILES : O=C(CCC=CCC=CCC=CCC=CCC=CCCC(CC)OS(=O)(=O)O[Na])OCC(COC(=O)CCCCCCCC=C
CCCCCCCCCC)OC(=O)CCCC=CCC=CCC=CCC=CCC=CCC
CHEM : Oils, fish,sulated, sodium salt
MOL FOR: C65 H103 O10 S1 Na1
MOL WT : 1099.59
------------------- SUMMARY (AOP v1.92): HYDROXYL RADICALS (25 deg C) --------
Hydrogen Abstraction = 48.2274 E-12 cm3/molecule-sec
Reaction with N, S and -OH = 0.0000 E-12 cm3/molecule-sec
Addition to Triple Bonds = 0.0000 E-12 cm3/molecule-sec
Addition to Olefinic Bonds = 507.6000 E-12 cm3/molecule-sec [Cis-isomer]
Addition to Olefinic Bonds = 576.0000 E-12 cm3/molecule-sec [Trans-isomer]
Addition to Aromatic Rings = 0.0000 E-12 cm3/molecule-sec
Addition to Fused Rings = 0.0000 E-12 cm3/molecule-sec
OVERALL OH Rate Constant = 555.8274 E-12 cm3/molecule-sec [Cis-isomer]
OVERALL OH Rate Constant = 624.2274 E-12 cm3/molecule-sec [Trans-isomer]
HALF-LIFE = 13.855 Min (12-hr day; 1.5E6 OH/cm3) [Cis-isomer]
HALF-LIFE = 12.337 Min (12-hr day; 1.5E6 OH/cm3) [Trans-isomer]
------------------- SUMMARY (AOP v1.91): OZONE REACTION (25 deg C) -----------
OVERALL OZONE Rate Constant = 117.000000 E-17 cm3/molecule-sec [Cis-]
OVERALL OZONE Rate Constant = 180.000000 E-17 cm3/molecule-sec [Trans-]
HALF-LIFE = 14.105 Min (at 7E11 mol/cm3) [Cis-isomer]
HALF-LIFE = 9.168 Min (at 7E11 mol/cm3) [Trans-isomer]
NOTE: Reaction with Nitrate Radicals May Be Important!
Experimental Database: NO Structure Matches
SMILES : HN(H)(H)OS(=O)(=O)OC(CCCCCCCC(=O)OCC(COC(=O)CCCCCCCC=CCCCCCCCC)OC(=O)
CCCCCCCC=CCCCCCCCC)CCCCCCCCC
CHEM : Oils, vegetable, sulfated, ammonium salts
MOL FOR: C57 H108 N1 O10 S1
MOL WT : 999.56
------------------- SUMMARY (AOP v1.92): HYDROXYL RADICALS (25 deg C) --------
Hydrogen Abstraction = 66.6693 E-12 cm3/molecule-sec
**Reaction with N, S and -OH = 0.0000 E-12 cm3/molecule-sec
Addition to Triple Bonds = 0.0000 E-12 cm3/molecule-sec
Addition to Olefinic Bonds = 112.8000 E-12 cm3/molecule-sec [Cis-isomer]
Addition to Olefinic Bonds = 128.0000 E-12 cm3/molecule-sec [Trans-isomer]
Addition to Aromatic Rings = 0.0000 E-12 cm3/molecule-sec
Addition to Fused Rings = 0.0000 E-12 cm3/molecule-sec
OVERALL OH Rate Constant = 179.4694 E-12 cm3/molecule-sec [Cis-isomer]
OVERALL OH Rate Constant = 194.6693 E-12 cm3/molecule-sec [Trans-isomer]
HALF-LIFE = 0.715 Hrs (12-hr day; 1.5E6 OH/cm3) [Cis-isomer]
HALF-LIFE = 0.659 Hrs (12-hr day; 1.5E6 OH/cm3) [Trans-isomer]
........................ ** Designates Estimation(s) Using ASSUMED Value(s)
------------------- SUMMARY (AOP v1.91): OZONE REACTION (25 deg C) -----------
OVERALL OZONE Rate Constant = 26.000000 E-17 cm3/molecule-sec [Cis-]
OVERALL OZONE Rate Constant = 40.000000 E-17 cm3/molecule-sec [Trans-]
HALF-LIFE = 1.058 Hrs (at 7E11 mol/cm3) [Cis-isomer]
HALF-LIFE = 0.688 Hrs (at 7E11 mol/cm3) [Trans-isomer]
NOTE: Reaction with Nitrate Radicals May Be Important!
Experimental Database: NO Structure Matches
SMILES : O=C(CCCCCCCC=CCCCCCCCC)OC(COC(=O)CCCCCCCC=CCCCCCCCC)COC(=O)CCCCCCCC(C
CCCCCCCC)OS(=O)(=O)O[Na]
CHEM : Oils, vegetable, sulfated, sodium salts
MOL FOR: C57 H105 O10 S1 Na1
MOL WT : 1005.52
------------------- SUMMARY (AOP v1.92): HYDROXYL RADICALS (25 deg C) --------
Hydrogen Abstraction = 66.6694 E-12 cm3/molecule-sec
Reaction with N, S and -OH = 0.0000 E-12 cm3/molecule-sec
Addition to Triple Bonds = 0.0000 E-12 cm3/molecule-sec
Addition to Olefinic Bonds = 112.8000 E-12 cm3/molecule-sec [Cis-isomer]
Addition to Olefinic Bonds = 128.0000 E-12 cm3/molecule-sec [Trans-isomer]
Addition to Aromatic Rings = 0.0000 E-12 cm3/molecule-sec
Addition to Fused Rings = 0.0000 E-12 cm3/molecule-sec
OVERALL OH Rate Constant = 179.4694 E-12 cm3/molecule-sec [Cis-isomer]
OVERALL OH Rate Constant = 194.6694 E-12 cm3/molecule-sec [Trans-isomer]
HALF-LIFE = 0.715 Hrs (12-hr day; 1.5E6 OH/cm3) [Cis-isomer]
HALF-LIFE = 0.659 Hrs (12-hr day; 1.5E6 OH/cm3) [Trans-isomer]
------------------- SUMMARY (AOP v1.91): OZONE REACTION (25 deg C) -----------
OVERALL OZONE Rate Constant = 26.000000 E-17 cm3/molecule-sec [Cis-]
OVERALL OZONE Rate Constant = 40.000000 E-17 cm3/molecule-sec [Trans-]
HALF-LIFE = 1.058 Hrs (at 7E11 mol/cm3) [Cis-isomer]
HALF-LIFE = 0.688 Hrs (at 7E11 mol/cm3) [Trans-isomer]
NOTE: Reaction with Nitrate Radicals May Be Important!
Experimental Database: NO Structure Matches
SMILES : HN(H)(H)OS(=O)(=O)OC(CC=CCCCCCCCC(=O)OCC(COC(=O)CCCCCCCC=CCC(O)CCCCCC
)OC(=O)CCCCCCCC=CCC(O)CCCCCC)CCCCCC
CHEM : Castor oil, sulfated, ammonium salt
MOL FOR: C57 H106 N1 O12 S1
MOL WT : 1029.54
------------------- SUMMARY (AOP v1.92): HYDROXYL RADICALS (25 deg C) --------
Hydrogen Abstraction = 81.0339 E-12 cm3/molecule-sec
**Reaction with N, S and -OH = 0.2800 E-12 cm3/molecule-sec
Addition to Triple Bonds = 0.0000 E-12 cm3/molecule-sec
Addition to Olefinic Bonds = 169.2000 E-12 cm3/molecule-sec [Cis-isomer]
Addition to Olefinic Bonds = 192.0000 E-12 cm3/molecule-sec [Trans-isomer]
Addition to Aromatic Rings = 0.0000 E-12 cm3/molecule-sec
Addition to Fused Rings = 0.0000 E-12 cm3/molecule-sec
OVERALL OH Rate Constant = 250.5139 E-12 cm3/molecule-sec [Cis-isomer]
OVERALL OH Rate Constant = 273.3139 E-12 cm3/molecule-sec [Trans-isomer]
HALF-LIFE = 0.512 Hrs (12-hr day; 1.5E6 OH/cm3) [Cis-isomer]
HALF-LIFE = 28.177 Min (12-hr day; 1.5E6 OH/cm3) [Trans-isomer]
........................ ** Designates Estimation(s) Using ASSUMED Value(s)
------------------- SUMMARY (AOP v1.91): OZONE REACTION (25 deg C) -----------
OVERALL OZONE Rate Constant = 39.000000 E-17 cm3/molecule-sec [Cis-]
OVERALL OZONE Rate Constant = 60.000000 E-17 cm3/molecule-sec [Trans-]
HALF-LIFE = 0.705 Hrs (at 7E11 mol/cm3) [Cis-isomer]
HALF-LIFE = 0.458 Hrs (at 7E11 mol/cm3) [Trans-isomer]
NOTE: Reaction with Nitrate Radicals May Be Important!
Experimental Database: NO Structure Matches
SMILES : O=C(CCCCCCCC=CCC(CCCCCC)OS(=O)(=O)O[Na])OCC(COC(=O)CCCCCCCC=CCC(O)CCC
CCC)OC(=O)CCCCCCCC=CCC(O)CCCCCC
CHEM : Castor oil, sulfated, sodium salt
MOL FOR: C57 H103 O12 S1 Na1
MOL WT : 1035.50
------------------- SUMMARY (AOP v1.92): HYDROXYL RADICALS (25 deg C) --------
Hydrogen Abstraction = 81.0339 E-12 cm3/molecule-sec
Reaction with N, S and -OH = 0.2800 E-12 cm3/molecule-sec
Addition to Triple Bonds = 0.0000 E-12 cm3/molecule-sec
Addition to Olefinic Bonds = 169.2000 E-12 cm3/molecule-sec [Cis-isomer]
Addition to Olefinic Bonds = 192.0000 E-12 cm3/molecule-sec [Trans-isomer]
Addition to Aromatic Rings = 0.0000 E-12 cm3/molecule-sec
Addition to Fused Rings = 0.0000 E-12 cm3/molecule-sec
OVERALL OH Rate Constant = 250.5139 E-12 cm3/molecule-sec [Cis-isomer]
OVERALL OH Rate Constant = 273.3139 E-12 cm3/molecule-sec [Trans-isomer]
HALF-LIFE = 0.512 Hrs (12-hr day; 1.5E6 OH/cm3) [Cis-isomer]
HALF-LIFE = 28.177 Min (12-hr day; 1.5E6 OH/cm3) [Trans-isomer]
------------------- SUMMARY (AOP v1.91): OZONE REACTION (25 deg C) -----------
OVERALL OZONE Rate Constant = 39.000000 E-17 cm3/molecule-sec [Cis-]
OVERALL OZONE Rate Constant = 60.000000 E-17 cm3/molecule-sec [Trans-]
HALF-LIFE = 0.705 Hrs (at 7E11 mol/cm3) [Cis-isomer]
HALF-LIFE = 0.458 Hrs (at 7E11 mol/cm3) [Trans-isomer]
NOTE: Reaction with Nitrate Radicals May Be Important!
Experimental Database: NO Structure Matches
Description of key information
Half-life for reaction with photochemically-produced hydroxyl radicals was estimated for sulfated oils representative molecules and resulted to be approximately 0.5 hours (OH concentration: 1.5E+06 OH radicals/cm3; Half-life: 12 h/day).
Key value for chemical safety assessment
- Half-life in air:
- 0.5 h
Additional information
The stability of representative molecules of sulfated oils in the atmosphere was estimated using the software AOPWIN (v 1.92). The molecules were predicted to be degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals. The half-life for this reaction in air resulted to range from 0.25 to 0.7 hours, with an average of approximately 0.5 hours, setting the following default values: OH concentration: 1.5E+06 OH radicals/cm3; Half-life: 12 h/day.
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