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Diss Factsheets
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EC number: 202-860-4 | CAS number: 100-52-7
- 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:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- GLP compliance:
- not specified
- Light source:
- not specified
- Reference substance:
- not specified
- Key result
- DT50:
- 9.4 h
- Remarks on result:
- other: data published in OECD SIDS dossier.
- Reaction with:
- OH radicals
- Rate constant:
- 0 cm³ molecule-1 s-1
- Transformation products:
- not specified
- Validity criteria fulfilled:
- yes
- Conclusions:
- The OECD SIDS (1994) dossier reported an OH radical reaction rate constant of 1.2e-11 cm3/molecule.second (reported to be equal to a DT50 of 9.4 hours) was calculated based on an estimated environmental OH radical concentration of 1.7e-6 radicals/cm3.
- Executive summary:
Data on the indirect photolysis (i.e. reaction with photochemically produced OH radicals) of benzaldehyde was published in the 1994 OECD SIDS Dossier for benzaldehyde. This data is originally from a paper published by Atkinson and Lloyds in 1984 in in which they reviewed evidence from many sources on the photochemical degradation of components of smog. No further information is known as the paper is not accessible. The OECD SIDS (1994) dossier reported an OH radical reaction rate constant of 1.2e-11 cm3/molecule.second (reported to be equal to a DT50 of 9.4 hours) was calculated based on an estimated environmental OH radical concentration of 1.7e-6 radicals/cm3.
- Endpoint:
- phototransformation in air
- Type of information:
- other: Publication/review of reported data
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Remarks:
- Peer reviewed pubication with well documented methods and data analysis.
- Qualifier:
- no guideline required
- Principles of method if other than guideline:
- The literature kinetic and mechanistic data for the gas-phase reactions of the OH radical with organic compounds (through 1988) have been tabulated, reviewed and evaluated over the entire temperature ranges for which data are available.
- Estimation method (if used):
- Two general experimental approaches, namely absolute and relative rate constant measurement methods, have been used to determine rate constants for the reactions of the OH radical with organic compounds. In the absolute technique, for the bimolecular reaction, either the psuedo-first order decay of one species is measured in the presence of a known excess concentration of the other reactant or the concentrations of both species are measured and the rate constant k is derived by calculation.
In the relative rate method, the rate constant of interest is determined relative to that for another reaction, normally a reaction of the OH radical with a second, or reference, species. Generally, the decay rates of two or more compounds are monitored in the presence of OH radicals, with other loss processes (chemical or physical) of these reactants being either quantitatively known or minimized. - Key result
- Reaction with:
- OH radicals
- Rate constant:
- 0 cm³ molecule-1 s-1
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The rate constant for the vapor-phase reaction of the test substance with photochemically-produced hydroxyl radicals has been reported to be 1.29E-11 cu cm/molecule-sec at 25 °C.
- Executive summary:
The literature kinetic and mechanistic data for the gas-phase reactions of the OH radical with organic compounds (through 1988) have been tabulated, reviewed and evaluated over the entire temperature ranges for which data are available. Atkinson (1989) identified two room temperature rate constants for benzaldehyde during this exercise and upon analysis found they were in general agreement. Therefore, the authors suggested that a unit-weighted average of these data should be used. This resulted in an overall OH rate constant for benzaldehyde of 1.29E-11 cu cm/molecule-sec at 25 ℃.
- Endpoint:
- phototransformation in air
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The photochemistry of the test substance has been studied by determining the quantum yields of benzene and carbon monoxide formation, the test substance consumption and phosphorescence emission, and by following the phosphorescence lifetime over a range of pressure and excitation wavelengths.
- GLP compliance:
- no
- Light source:
- other: UV light
- Light spectrum: wavelength in nm:
- 265 - 380
- Details on light source:
- Most photolyses were carried out using cylindrical quartz optical cells 100 mm long and 22 mm in diameter. Photolyses were effected with a high pressure mercury are in conjunction with a monochromator set so that the spectral bandwidth was 1.6 nm. For emission and lifetime measurements rectangular 10-mm path length flouresence cells were used.
- Details on test conditions:
- The experiment was conducted at room temperature, 22±2 °C.
- Reference substance:
- not specified
- Test performance:
- No information provided
- Quantum yield (for direct photolysis):
- 0.4
- Transformation products:
- yes
- No.:
- #1
- No.:
- #2
- Validity criteria fulfilled:
- yes
- Conclusions:
- Although the absorption is relatively weak, the quantum yield (which is approximately 0.34-0.41) is quite high and it suggests that the test substance may directly photolyze in the environment.
- Executive summary:
The photochemistry of the test substance has been studied by determining the quantum yields of benzene and carbon monoxide formation, the test substance consumption and phosphorescence emission, and by following the phosphorescence lifetime over a range of pressure and excitation wavelengths. Although the absorption is relatively weak, the quantum yield (which is approximately 0.34-0.41) is quite high and it suggests that the test substance may directly photolyze in the environment.
Referenceopen allclose all
The OECD SIDS (1994) dossier reported an OH radical reaction rate constant of 1.2e-11 cm3/molecule.second (reported to be equal to a DT50 of 9.4 hours) was calculated based on an estimated environmental OH radical concentration of 1.7e-6 radicals/cm3. This data was taken from a review paper by Atikinson and Lloyds (1984).
Atkinson (1989) identified two room temperature rate constants and upon analysis found they were in general agreement. Therefore, the authors suggested that a unit-weighted average of these data should be used. This resulted in an overall OH rate constant = 1.29E-11 cu cm/molecule-sec at 25 ℃.
Description of key information
A DT50 of 9.4 h has been predicted for the indirect photolysis of benzaldehyde in air caused by reaction with photochemically produced hydroxyl radicals.
A DT50 of 16.4 days has been predicted for the indirect photolysis of benzaldehyde in air caused by reaction with photochemically produced nitrate radicals.
Direct photolysis of benzaldehyde in air is possible but may be slow and benzene and carbon monoxide and a yellowish polymer have been identified as transformation products.
Key value for chemical safety assessment
- Half-life in air:
- 9.4 h
- Degradation rate constant with OH radicals:
- 1.29 cm³ molecule-1 s-1
Additional information
Indirect photolysis in air by OH radicals
Data on the indirect photolysis (i.e. reaction with photochemically produced hydroxyl (OH) radicals) of benzaldehyde in air have been reported in two separate collation and review papers. Atkinson (1989) reported two room temperature rate constants for benzaldehyde and suggested that a unit-weighted average of these two data points was valid. This resulted in an overall OH rate constant for benzaldehyde of 1.29E-11 cm3/molecule/second at 25℃. Atkinson and Lloyds (1984) also reported an OH radical reaction rate constant of 1.2e-11 cm3/molecule/second, no further information is known as the paper is not accessible. In the 1994 OECD SIDS Dossier for benzaldehyde, the Atkinson and Lloyds (1984) value was quoted and reported to be equal to a DT50 of 9.4 hours (based on an estimated environmental OH radical concentration of 1.7e-6 radicals/cm3). As these two OH radicle reaction rates are comparable and the OECD is considered an authoritative resource, DT50 of benzaldehyde in the atmosphere following indirect photolysis by OH radicals is considered to be 9.4 days. This is further supported by the QSAR produced by the Episuite program which predicted a DT50 of 7.18 hours.
Atkinson et al. (1987) reported a reaction rate for indirect photolysis by photochemically produced nitrate (NO3) radicals in air of 2.0E-15 cu cm/molecule-sec at 25 °C, which corresponds to a DT50 of 16.7 days based on an atmospheric concentration of 2.4E+8 NO3 radicals/cm3 (as quoted by HSDB).
Direct photolysis in air
The available studies show that direct photolysis of benzaldehyde in air is possible but may be slow. Benzene and carbon monoxide and a yellowish polymer have been identified as transformation products following direct photolysis of benzaldehyde in air.
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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