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Diss Factsheets
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EC number: 201-152-2 | CAS number: 78-87-5
- 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:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2003
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- No method available
- GLP compliance:
- not specified
- Light source:
- not specified
Reference
Photo-oxidation half-life in air, based on estimated rate constant for the vapour phase reaction with hydroxyl radicals in air, in the range 65 - 646 hr.
1,2-Dichloropropane does not have any chromophores that absorb wavelengths >290 nm, so direct photolysis will not be a significant fate process. Vapour phase photolysis under simulated sunlight did not occur after prolonged exposure (period not stated). Experimental determination of its rate of reaction with hydroxyl radicals gave a half-life of >23 days. A computer estimate of its half-life due to H-atom abstraction by hydroxyl radical yields a calculated half-life of 7.12 days.
Description of key information
Key value for chemical safety assessment
- Half-life in air:
- 23 d
Additional information
Photo-oxidation half-life in air, based on estimated rate constant for the vapour phase reaction with hydroxyl radicals in air, in the range 65 - 646 hr.
1,2-Dichloropropane does not have any chromophore groups that absorb wavelengths >290 nm, so direct photolysis will not be a significant fate process. Vapour phase photolysis under simulated sunlight did not occur after prolonged exposure (period not stated). Experimental determination of its rate of reaction with hydroxyl radicals gave a half-life of >23 days. A computer estimate of its half-life due to H-atom abstraction by hydroxyl radical yields a calculated half-life of 7.12 days.
Based on a review of the available data for1,2-dichloropropaneand for its structural analogue,1,2-dichloroethane, Kurland (2004) evaluated the potential of1,2-dichloropropaneto contribute to global warming (GWP), to photochemical ozone creation (POCP), and to ozone depletion (ODP), including a review of the available data on hydroxyl radical reaction rate for1,2-dichloropropane.
Photodegradation will account for some removal of 1,2-dichloropropane from the atmosphere. This is based on a calculated hydroxyl radical reaction rate of 5.2 x10-13 cm3molecule-1s-1(Yujing and Mellouki, 2001), which was in excellent agreement with a measured value of 4.6±0.6 x 10-13cm3 molecule-1s-1 (Atkinson, R., 1987; Kwok and Atkinson, 1995). The lifetime (τ=1/(k[OH]) of 1,2-dichloropropane, was estimated by using a global tropospheric 24-hour average OH radical concentration of 1x106molecule cm-3 (Hein et al., 1997) and the measured bimolecular rate constant at room temperature. The tropospheric lifetime of 25 days is in good agreement with another reported value of 27 days (Tauzon et al., 1984) and is relatively short. Kurland (2004) concluded that the products of oxidation of 1,2-dichloropropane will not result in the introduction of chlorine into the stratosphere, and that potential contributions of 1,2-dichloropropane to Global Warning, POCP, or ODP, were negligible
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