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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

Endpoint summary
Administrative data
Link to relevant study record(s)
Description of key information
Short description of key information on bioaccumulation potential result:
L-, DL, and unspecified Menthol isomers were well absorbed via the oral (dermal 100 % assumtion) route of exposure. They were mainly excreted as glucuronic acid conjugates. In rats an extensive enterohepatic circulation leads in addition to various hydoxylated degradation products. Glucuronides and degradation products were mainly eliminated via urine, minor quantities via the faeces. Thus, both in animals and humans menthol seems to be metabolized in a similar way, being rapidly glucuronidated and excreted mainly via urine.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
L-, DL, and unspecified Menthol isomers were well absorbed via the oral rout and as a worst case assumption also by dermal route. They were mainly excreted as glucuronic acid conjugates. Glucuronides and degradation products were fast eliminated mainly via urine, minor quantities via the faces. In one study reliable 1 study the total excretion in rats was after 17 h was 56,5% of given dose correlating to about 90% of the recoverd Menthol activity. Additional recovered activity was found in ileum 3.5%, fat 2.1 %, liver 0.8%, Serum 0.31%,Kidney 0.2%, Brain < 0.1%, Testis < 0.1%. Administrated menthol in soft gelatine capsuls to human probands was fast absorbed and excreted (halflife of excetrion 2 -4h).
Menthol glycuronic acid appeared in the urine of rabbits in less than an hour after gavage dosing menthol, and 90 per cent of the conjugated acid was found to be excreted in 6 hours when 2 g of menthol were feed. Even when larger doses were given over 90 per cent of the total amount excreted appeared in the urine during the first 24 hours.
Thus, both in animals and humans the Menthols can be metabolized in similar way, being rapidly glucuronidated and excreted mainly via urine.A toxicokinetic assessment in more detail is presented in attachment MentholsTK_Assessment_Final.pdf of section Basic toxicokinetics.
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