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EC number: 242-060-2 | CAS number: 18172-67-3
- 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
90-day inhalation toxicity study conducted in rats showed a LOAEL of 50 ppm for males based on male specific renal effects linked to alpha2µ-globulin accumulation and a NOAEL of 200 ppm for females based on mortality and a lower body weight gain. Mortality was observed in female rats in the high dose group. As no specific target organ was sufficiently impaired by the treatment to cause mortality, it may be concluded that these deaths have a general systemic toxicity origin.
90-day inhalation toxicity study conducted in mice showed a NOAEL in male and female mice of 50 ppm based on minimal to moderate hyperplasia observed in the transitional epithelium of the urinary bladder in animals treated at 100 ppm and higher doses.
Key value for chemical safety assessment
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Dose descriptor:
- NOAEC
- 283.24 mg/m³
- Study duration:
- subchronic
- Species:
- mouse
Additional information
90-day inhalation toxicity study conducted in rats showed a LOAEL of 50 ppm for males based on male specific renal effects linked to alpha2µ-globulin accumulation and a NOAEL of 200 ppm for females based on mortality and a lower body weight gain. Mortality was observed in female rats in the high dose group. As no specific target organ was sufficiently impaired by the treatment to cause mortality, it may be concluded that these deaths have a general systemic toxicity origin.
90-day inhalation toxicity study conducted in mice showed a NOAEL in male and female rats of 50 ppm based on minimal to moderate hyperplasia observed in the transitional epithelium of the urinary bladder in animals treated at 100 ppm and higher doses.
As the accumulation of alpha2μ-globulin in renal proximal tubule cells observed in male rats is sex and species-specific, the LOAEL defined for male rats is not relevant for humans (Meek, 2003). Thus, the NOAEL selected is based on minimal to moderate hyperplasia observed in the transitional epithelium of the urinary bladder found in mice at 100 ppm and higher doses.
NOAEC mouse inhalation (mg/m3) = (NOAEL (mg/kg bw/day) * molecular weight) / Vmol = (50 * 136.24) / 24.05 = 283.24 mg/m3
Reference: Meek M.E. et al. (2003) A Framework for Human Relevance Analysis of Information on Carcinogenic Modes of Action, Critical Reviews in Toxicology, 33(6): 591 -653.
Repeated dose toxicity: inhalation - systemic effects (target organ) urogenital: urinary bladder
Justification for classification or non-classification
The CLP classification for Specific Target Organ Toxicity in repeated exposure is based on results found in rats therefore the results found in mice are not taken into account. The LOAEL in male rats is the lowest dose level tested, but it is not relevant to humans as it is based on renal effects linked to alpha2µ-globulin accumulation. When considering effects other than those on kidneys in males, a lower body weight gain was observed at 400 ppm when compared to controls. A NOAEL could be defined in female rats at 200 ppm on the basis of mortality and a lower body weight gain at the next dose level when compared to controls. The overall NOAEL relevant for humans is 200 ppm.
Although the NOAEL relevant for humans is 200 ppm and the limit dose for Specific Target Organ Toxicity in repeated exposure classification according to CLP regulation is 250 ppm, there is no critical adverse effects identified in a specific target organ that could lead to classification for Specific Target Organ Toxicity in repeated exposure.
Therefore, considering read across approach, (-)-beta-pinene does not need to be classified Category 2 for Specific Target Organ Toxicity in repeated exposure according to CLP Regulation (EC) No 1272/2008.
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