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EC number: 939-412-9 | CAS number: 85586-38-5
- 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
- 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
- Principles of method if other than guideline:
- Calculation based on AOPWIN v1.92a, Estimation Programs Interface Suite™ for Microsoft® Windows v 4.11. US EPA, United States Environmental Protection Agency, Washington, DC, USA.
- Estimation method (if used):
- PHOTOCHEMICAL REACTION WITH OH RADICALS
- Concentration of OH radicals: 0.5 E+06 radicals/cm3
- Degradation rate constant: 20.5 E-12 cm3/molecule-sec
- Temperature for which rate constant was calculated: 25 °C
- Computer programme: AOPWIN v1.92a - Key result
- DT50:
- 19 h
- Test condition:
- calculation based on a 24 h day
- Validity criteria fulfilled:
- not applicable
- Endpoint:
- phototransformation in air
- 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 valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Principles of method if other than guideline:
- Calculation based on AOPWIN v1.92a, Estimation Programs Interface Suite™ for Microsoft® Windows v 4.11. US EPA, United States Environmental Protection Agency, Washington, DC, USA.
- Estimation method (if used):
- PHOTOCHEMICAL REACTION WITH OH RADICALS
- Concentration of OH radicals: 0.5 E+06 radicals/cm3
- Degradation rate constant: 23.3 E-12 cm3/molecule-sec
- Temperature for which rate constant was calculated: 25 °C
- Computer programme: AOPWIN v1.92a - Key result
- DT50:
- 17 h
- Test condition:
- calculation based on a 24 h day
- Validity criteria fulfilled:
- not applicable
- Endpoint:
- phototransformation in air
- 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 valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Principles of method if other than guideline:
- Calculation based on AOPWIN v1.92a, Estimation Programs Interface Suite™ for Microsoft® Windows v 4.11. US EPA, United States Environmental Protection Agency, Washington, DC, USA.
- Estimation method (if used):
- PHOTOCHEMICAL REACTION WITH OH RADICALS
- Concentration of OH radicals: 0.5E+06 radicals/cm3
- Degradation rate constant: 17.7E-12 cm3/molecule-sec
- Temperature for which rate constant was calculated: 25 °C
- Computer programme: AOPWIN v1.92a
- Key result
- DT50:
- 22 h
- Test condition:
- calculation based on a 24 h day
- Validity criteria fulfilled:
- not applicable
- Endpoint:
- phototransformation in air
- 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 valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Principles of method if other than guideline:
- Calculation based on AOPWIN v1.92a, Estimation Programs Interface Suite™ for Microsoft® Windows v 4.11. US EPA, United States Environmental Protection Agency, Washington, DC, USA.
- Estimation method (if used):
- PHOTOCHEMICAL REACTION WITH OH RADICALS
- Concentration of OH radicals: 0.5 E+06 radicals/cm3
- Degradation rate constant: 9.2 E-12 cm3/molecule-sec
- Temperature for which rate constant was calculated: 25 °C
- Computer programme: AOPWIN v1.92a - Key result
- DT50:
- 42 h
- Test condition:
- calculation based on a 24 h day
- Validity criteria fulfilled:
- not applicable
- Endpoint:
- phototransformation in air
- 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 valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Principles of method if other than guideline:
- Calculation based on AOPWIN v1.92a, Estimation Programs Interface Suite™ for Microsoft® Windows v 4.11. US EPA, United States Environmental Protection Agency, Washington, DC, USA.
- Estimation method (if used):
- PHOTOCHEMICAL REACTION WITH OH RADICALS
- Concentration of OH radicals: 0.5 E+06 radicals/cm3
- Degradation rate constant: 12 E-12 cm3/molecule-sec
- Temperature for which rate constant was calculated: 25 °C
- Computer programme: AOPWIN v1.92a
- Key result
- DT50:
- 32 h
- Test condition:
- calculation based on a 24 h day
- Validity criteria fulfilled:
- not applicable
- Endpoint:
- phototransformation in air
- 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 valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Principles of method if other than guideline:
- Calculation based on AOPWIN v1.92a, Estimation Programs Interface Suite™ for Microsoft® Windows v 4.11. US EPA, United States Environmental Protection Agency, Washington, DC, USA.
- Estimation method (if used):
- PHOTOCHEMICAL REACTION WITH OH RADICALS
- Concentration of OH radicals: 0.5E+06 radicals/cm3
- Degradation rate constant: 14.8 E-12 cm3/molecule-sec
- Temperature for which rate constant was calculated: 25 °C
- Computer programme: AOPWIN v1.92a - Key result
- DT50:
- 26 h
- Test condition:
- calculation based on a 24h day
- Validity criteria fulfilled:
- not applicable
- Endpoint:
- phototransformation in air
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Justification for type of information:
- Read across justification is attached in chapter 13.
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Key result
- DT50:
- 42 h
- Remarks on result:
- other: CAS 142-31-4 (C8)
- Key result
- DT50:
- 32 h
- Remarks on result:
- other: CAS 142-87-0 (C10)
- Key result
- DT50:
- 26 h
- Remarks on result:
- other: CAS 151-21-3 (C12)
- Key result
- DT50:
- 22 h
- Remarks on result:
- other: CAS 1191-50-0 (C14)
- Key result
- DT50:
- 19 h
- Remarks on result:
- other: CAS 1120-01-0 (C16)
- Key result
- DT50:
- 17 h
- Remarks on result:
- other: CAS 1120-04-3 (C18)
Referenceopen allclose all
For detailed description on the model and its applicability, see "Any other information on materials and methods incl. tables". Result refers to the uncharged molecule. The estimation is based on a 24h day.
For detailed description on the model and its applicability, see "Any other information on materials and methods incl. tables". Result refers to the uncharged molecule. The estimation is based on a 24h day.
For detailed description on the model and its applicability, see "Any other information on materials and methods incl. tables". Result refers to the uncharged molecule. The estimation is based on a 24h day.
For detailed description on the model and its applicability, see "Any other information on materials and methods incl. tables". Result refers to the uncharged molecule. The estimation is based on a 24h day.
For detailed description on the model and its applicability, see "Any other information on materials and methods incl. tables". Result refers to the uncharged molecule. The estimation is based on a 24h day.
Description of key information
DT50 between 22 hours and 42 hours (EPISuite calculation for constituents)
Key value for chemical safety assessment
Additional information
Since no information on photodegradation of C8-18AS Mg & TEA (CAS 85586-38-5) is available, in accordance to Regulation (EC) No. 1907/2006 Annex XI, 1.5 Grouping of substances, a read-across to to the constituents of the test substance was conducted. Read-across data from C8AS Na (CAS 142-31-4), C10AS Na (CAS 142-87-0), C12AS Na (CAS 151-21-3), C14AS Na (CAS 1191-50-0) C16AS Na (CAS 1120-01-0) and C18AS Na (CAS 1120-04-3) were used. The half-life time in the air was assessed based on the calculation method using EPI Suite v 4.11, AOPWIN v 1.92a.
The half-life time in the air is:
For C8AS Na: 42 hours
For C10AS Na: 32 hours
For C12AS Na: 26 hours
For C14AS Na: 22 hours
For C16AS Na: 19 hours
For C18 AS Na: 17 hours
Based on the above data it can be concluded that the half-life of C8-18AS Mg & TEA (CAS 856586-38-5) in the air is between 17 hours and 42 hours.
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