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EC number: 216-721-0 | CAS number: 1653-19-6
- 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
There are no standard studies on the repeated dose toxicity of 2,3 dichloro-1,3 butadiene following oral or dermal exposures. No effects attributed to 2,3 dichloro-1,3 butadiene were observed in a sub-acute repeated dose inhalation study in which rats were exposed to vapours at 0.4 mg/l. In a one-generation, repeated dose inhalation exposures to 2,3 dichloro-1,3 butadiene at 0, 1, 5 or 50 ppm, A NOEL of 5 ppm (25 mg/m3) was reported based on observations of decreased body weight, weight gain and food consumption parameters and degeneration of the nasal olfactory epithelium at 50 ppm.
Key value for chemical safety assessment
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Dose descriptor:
- NOAEC
- 25 mg/m³
- Study duration:
- subchronic
- Species:
- rat
Additional information
There are no standard studies on the repeated dose toxicity of 2,3 dichloro-1,3 butadiene following oral or dermal exposures.
No effects attributable to 2,3 dichloro-1,3 butadiene were observed in a sub-acute repeated dose inhalation study, in which 10 male Crl:Cd rats were exposed to vapours at a concentrations of 0.4 mg/l for 6 hours/day, 5 days/week for 2 weeks (control rats were simultaneously exposed to air only). No effects on clinical parameters or microscopic changes were observed in treated rats. Although liver mitotic parameters were slightly increased following the 10th exposure, levels were normal following 14 days of recovery. The significance of this change is not clear since no other morphologic alterations were observed. The mean relative liver weights of treated rats were significantly higher that controls after the 10th exposure but were normal after 14 days of recovery. Treated rats had significantly lower body weights than controls during the exposure period, but showed a normal rate of weight gain during recovery. The relative testing weights of test rats were significantly higher than that of controls after 14 days recovery. In the absence of any microscopic changes, the relevance of this weight change is questionable
The sub-chronic repeated dose inhalation toxicity of 2,3 dichloro-1,3 butadiene was investigated in a one-generation fertility and early embryonic developmental study in which groups of Crl:CD®(SD)IGS BR rats (24/sex/concentration) were exposed by whole body inhalation to vapours at 0, 1, 5, or 50 ppm. Rats were exposed for 6 hours/day during premating (8 weeks; 5 days/week), during cohabitation of mating pairs (up to 2 weeks, 7 days/week), and then post-cohabitation for males and nonpregnant females (approximately 7 days, 7 days/week). The pregnant dams were exposed from conception to implantation (days 0-7 of gestation). In parental rats, no treatment-related effects were observed on mortality, clinical parameters, oestrous cycle and sperm parameters, mating, precoital interval and fertility, gross observations and organ weights. Treatment-related effects evident at 50 ppm were decreased body weight and weight gain, food consumption and efficiency and degeneration of the nasal olfactory epithelium.
The no-observed-effect level (NOEL) for the sub-chronic repeated dose inhalation toxicity of 2,3 dichloro-1,3 butadiene in rats was reported as 5 ppm (25 mg/m3) based on observations of reduced body weight, bodyweight gain and food consumption parameters and degeneration of the nasal olfactory epithelial toxicity at 50 ppm.
Repeated dose toxicity: inhalation - systemic effects (target organ) respiratory: nose
Justification for classification or non-classification
There is insufficient evidence to classify 2,3 dichloro-1,3 butadiene for repeated dose toxicity
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