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EC number: 218-690-9 | CAS number: 2216-51-5
- 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
Carcinogenicity
Administrative data
Description of key information
In a combined repeated dose/carcinogenicity study (NCI, 1979), in both dose groups (0.375% and 0.75% DL Menthol in diet of rats and 0.2 and 0.4% in the diet of mice), neither toxicity nor carcinogenicity in Fischer 344 rats or B6C3F1 mice was found after 103 weeks exposure. The mean body weights of the dosed rats and mice were slightly lower than those of corresponding controls. This could be explained by less palatability of the Menthol containing food combined with a smaller feed uptake.
Key value for chemical safety assessment
Carcinogenicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 375 mg/kg bw/day
- Study duration:
- chronic
- Species:
- rat
Justification for classification or non-classification
L Menthol does not meet the criteria for classification and labelling for carcinogenicity, as set out in Regulation (EC) NO. 1272/2008 and Directive 67/548/EEC.
Additional information
Justification for Read-across:
Based on the identical profiles of the different Menthols we can use them for read across studies as laid out in detail in the Read-Across Justification for Menthols (see file MentholsReadAcrossFinal.pdf in section 13). These isomers are L Menthol (CAS 2216-51-5), D Menthol (CAS 15356-60-2) and DL Menthol (CAS 89-78-1).
Moreover, a comparative physico-chemical profile of these isomers reinforces this similarity. As structural isomers, the members of the menthol category share the same molecular weight. Of particular importance to environmental effects and human effects are the values for partition coefficient (log Kow around 3), vapour pressure (from 17 Pa at 25°C for the DL Menthol to 21 Pa 25°C for the natural L Menthol ) and water solubility ( moderately soluble from 410 mg/l at 25°C for the natural L Menthol to 470 mg/l at 25°C for the DL Menthol). The read across is consistent based on these physico-chemical parameters.
In OECD SIDS, L Menthol (CAS 2216-51-5), D Menthol (CAS 15356-60-2) and DL Menthol (CAS 89-78-1) were recognized as a category group. Investigations on toxicokinetics show that L-, DL- and the unspecified Menthol are well absorbed via the oral route. For all of the isomers, elimination is rapid and mainly occurs as glucuronic acid conjugates via urine, minor amounts via faeces. Significant differences in toxicokinetic properties of Menthol isomers were not reported.
The available toxicity data indicate very similar toxicity profiles for D-, L-, DL Menthol and the unspecified Menthol isomer mixture. In mammalian species the low toxicity was manifested in LD50 values generally greater than 2000 mg/kg bw in acute studies, limited toxicity in repeated dose studies, and no effects in teratology evaluations. Irritation to skin and eyes was slight to moderate. DL Menthol is a racemic mixture of D- and L- isomers and contains both isomers in equal proportion. Data gaps for L Menthol can therefore be filled by the respective results with the racemic mixture and or results of the D Menthol isomer respectively.
Due to above discussion, to this endpoint, carcinogenic properties of L Menthol can be thought equivalent to the tested substance DL Menthol.
Key study:
In a combined repeated dose/carcinogenicity study (NCI, 1979), in both dose groups (0.375% or 0.75% DL Menthol in diet of rats and 0.2 or 0.4% in the diet of mice), neither toxicity nor carcinogenicity in Fischer 344 rats or B6C3F1 mice was found after 103 weeks exposure.
In male rats, no tumors occurred at incidences which were considered to be associated with the administration of DL Menthol.
In female rats, no tumors occurred at higher incidences in dosed groups than in control groups. Fibroadenomas of the mammary gland occurred at lower incidences in the low-dose (10/49) and high-dose (7/49) groups than in the control group (20/50), and alveaolar/bronchiolar adenomas or carcinomas of the lung occurred only in the controls (3/50).
In mice of either sex, no tumors occurred in dosed groups at incidences that were significantly different from those for corresponding control groups.
(highest tested dose levels in rats approx. 375 mg/kg bw/day, in mice approx. 667 mg/kg bw/day). Since DL Menthol contains the two isomers in a 50:50 ratio it can be assumed that neither L- nor D Menthol had carcinogenic properties.
Justification for selection of carcinogenicity via oral route endpoint:
The mean body weights of the dosed rats and mice were slightly lower than those of corresponding controls. This could be explaied by less palatability of the Menthol containing food combined with a smaller feed uptake. No other clinical signs related to administration of DL Menthol were noted in any dosed groups of rats and mice.
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