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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
Endpoint summary
Administrative data
Description of key information
Additional information
1,2-Dichloropropane undergoes reactions with hydroxyl radicals in the atmosphere. The calculated half-life of 1,2-dichloropropane due to this reaction is 34.9 days at based on an OH radical concentration of 5E5 OH/cm3, a 24 hour photoday, and an overall OH-rate constant of 4.6E-13 cm3/molecule-sec (298 K). Direct photolysis is not an important process.
Hydrolysis is not expected to be an important removal process for 1,2-dichloropropane. The half-life for this reaction in water (pH 6.9) is 283 months at 25 C (Milano et al., 1988). Hydrolysis products detected include 1-chloro-2-propanol and hydrochloric acid. The reaction is faster in seawater (pH 8.3) with a half-life of 60 months at 25 C.
Direct photolysis of 1,2-dichloropropane in water is not likely to be a significant removal process, since the molecule does not have chromophores which absorb wavelengths > 290 nm.
The results of biodegradation screening tests are variable. 1,2-Dichloropropane was not degraded in the Zahn-Wellens Test for inherent biodegradability. No degradation was also observed in the Modified MITI Test (301C). However, based on the supporting studies, 1,2-dichloropropane is susceptible to biodegradation under aerobic conditions when incubated with adapted cultures, particularly those containing microbial oxygenase enzymes with broad substrate specificity.
1,2-Dichloropropane was degraded in water and sediment by naturally occurring organisms under anaerobic conditions. Studies conducted with sediments from Red Cedar Creek demonstrated stochiometric conversion to propene after 4 months of incubation. Based on these results, the estimated half-life in surface sediments is 60 days at 25 C.
Half-lives for the dissapation of 1,2-dichloropropane in soils range from 41 to 69 days (average 52 days) at 15C. Based on the release rates of water extractable inorganic chloride, the complete degradation of 1,2-dichloropropane is slow.
Bioaccumulation of 1,2-dichloropropane does not appear to occur to a significant extent. Measured bioconcentration factors (BCF) ranged from 0.5 to 6.9.
Soil adsorption coefficients (Koc) for 1,2-dichloropropane have been calculated using various equations based on the relationship between Koc and either water solubility or octanol-water partition coefficient. Reported values for Koc range from 46.9 to 299.14. The value estimated using a widely accepted quantitative structure activity relationship was taken as the key parameter (Koc = 60.3).
The Henry’s Law constant for 1,2-dichloropropane has been measured experimentally at different temperatures. The experimental values were generally consistent and in excellent agreement with calculated values. The measured value of 2.82 x 10e-3 atm-m3/mol at 25 C was taken as representative.
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