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EC number: 202-423-8 | CAS number: 95-48-7
- 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 ā 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
Carcinogenicity
Administrative data
Description of key information
There are no bioassays or chronic studies available to assess the
carcinogenic potential of o-cresol.
From tumour promotion studies in mice there are some indications that
cresol may act as promotor (Boutwell and Bosch 1959). In cell
transformation assays in vitro the transforming activity of o-cresol was
evaluated as inconclusive in the presence of a metabolic activation
system (CMA 1989) whereas without a metabolic activation system no
activity was detected (Pepper, Hamilton and Scheetz 1981).
Key value for chemical safety assessment
Carcinogenicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
According to CLP classification criteria (Regulation (EC) No 1272/2008) a classification is not justified.
Additional information
There are no bioassays or chronic studies available to assess the carcinogenic potential of o-cresol.
From tumour promotion studies in mice there are some indications that cresol may act as promotor (Boutwell and Bosch 1959). Due to limited information on materials and methods, insufficient characterisation of test compond, benzene as solvent and acute toxicity of the applied doses, the study is not assignable. In cell transformation assays in vitro the transforming activity of o-cresol was evaluated as inconclusive in the presence of a metabolic activation system (CMA 1989) whereas without a metabolic activation system no activity was detected (Pepper, Hamilton and Scheetz 1981).
The tumor-promoting ability of o-cresol using the mouse skin-painting model was investigated (Boutwell & Bosch, 1959). Both the average number of skin papillomas per mouse and the percentage of exposed mice with at least one papilloma were increased by treatment with o-cresol. No carcinomas were observed. It should be noted that the vehicle used was benzene, a known carcinogen. The presence of benzene did not appear to affect the results, however, since no papillomas were observed in benzene treated controls. This study suggests cresols may act as promoters (OECD SIDS o-Cresol, CAS NĀ°: 95-48-7, UNEP publication).
Cresols have not been evaluated for ability to induce cancer when applied to the skin of animals. However, a study of skin tumor promotion by cresols was located (Boutwell and Bosch 1959). 27 to 29 mice were given a single dermal application of 9,10-dimethyl-1,2-benzanthracene (DMBA), a cancer initiator, followed by application of 20% solutions of o-, p-, or m-cresol in benzene twice a week for 12 weeks. This level of cresols exposure proved to be acutely toxic, producing relatively high nontumor-related mortality. Consequently, all tumor results were based on number of survivors (14ā20 per group). Promotion with cresols led to increases in the average number of skin papillomas per mouse and the percentage of exposed mice with at least one papilloma. o-Cresol was the most potent isomer, and p-cresol the least. Carcinomas were not observed following cresols exposure, although the observed papillomas have the potential to develop into carcinomas. A problem with the study was use of benzene, a known carcinogen, as the solvent for the cresols. However, benzene controls in the cresols experiment did not develop papillomas, and neither did benzene controls in four parallel series of experiments (a few papillomas were observed in a fifth benzene control group). Therefore, the results of this study showing that all three cresol isomers are capable of promoting skin tumors initiated by DMBA appear to be valid (U.S. DEPART- MENT OF HEALTH AND HUMAN SERVICES, Public Health Service, Agency for Toxic Substances and Disease RegistrySeptember 2008).
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