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EC number: 283-406-2 | CAS number: 84625-32-1 Extractives and their physically modified derivatives such as tinctures, concretes, absolutes, essential oils, oleoresins, terpenes, terpene-free fractions, distillates, residues, etc., obtained from Eucalyptus globulus, Myrtaceae.
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Study period:
- 1986
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study well documented, meets generally accepted scientific principles, acceptable for assessment
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 986
Materials and methods
- Objective of study:
- metabolism
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- In vivo metabolism study, following oral (gavage) administration in rats.
- GLP compliance:
- no
Test material
- Reference substance name:
- Cineole
- EC Number:
- 207-431-5
- EC Name:
- Cineole
- Cas Number:
- 470-82-6
- Molecular formula:
- C10H18O
- IUPAC Name:
- 1,3,3-trimethyl-2-oxabicyclo[2.2.2]octane
- Test material form:
- not specified
- Details on test material:
- - Name of test material (as cited in study report): Cineole
- Analytical purity: 99 % (GLC analysis)
Constituent 1
- Radiolabelling:
- no
Test animals
- Species:
- rat
- Strain:
- not specified
- Sex:
- male
Administration / exposure
- Route of administration:
- other: oral - gastric intubation
- Vehicle:
- other: 1 % methyl cellulose
- Duration and frequency of treatment / exposure:
- Once daily for 20 days
Doses / concentrations
- Remarks:
- Doses / Concentrations:
800 mg/kg bw/day
- No. of animals per sex per dose / concentration:
- No data
- Control animals:
- yes, concurrent vehicle
Results and discussion
Main ADME results
- Type:
- metabolism
- Results:
- hydroxylated derivatives of Cineol such as 2-hydroxy cineole and 3-hydroxy cineole are excreted as conjugates
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- Not applicable
- Details on distribution in tissues:
- Not applicable
- Details on excretion:
- Not applicable
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- - The acid methyl esters (250 mg) were subjected to TLC which showed the presence of one major compound i.e., methyl ester of 1,8-dihydroxy -10-carboxy p-methane and three minor compounds. The TLC analysis of the neutral fraction (200 mg) showed the presence of one major i.e., 2-hydroxy cineole and two minor metabolites. The neutral fraction (500 mg) obtained from hydrolysed urine on TLC analysis revealed the presence of two major (similar to 2-hydroxy cineole and 3-hydroxy cineole) and two minor metabolites.
- Based on the results, it is rather difficult to predict the sequence of reactions taking place during the biotransformation of cineole. However, one can envisage the formation of 1,8-dihydroxy-10-carboxy-p-methane through the intermediary of p-methane 1,8-diol and further metabolism is possibly initiated by the oxygenation of the C-10 methyl group resulting in the formation of p-methane-1,8,10-triol which undergoes stepwise oxidation to the corresponding aldehydes and then to an acid.
Bioaccessibility (or Bioavailability)
- Bioaccessibility (or Bioavailability) testing results:
- Not applicable
Any other information on results incl. tables
None
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): other: hydroxylated derivatives of Cineol such as 2-hydroxy cineole and 3-hydroxy cineole are excreted as conjugates
Cineole was metabolised to hydroxylated derivatives such as 2-hydroxy cineole and 3-hydroxy cineole in rats and are excreted as conjugates. - Executive summary:
In an in vivo metabolism study, 1,8-Cineole was administered by oral route (via gastric intubation) to male albino rats at the dose of 800 mg/kg bw/day once daily for 20 days as a suspension in 1 % methyl cellulose solution. Control rats were given only with vehicle (4 mL/kg bw/day). Urine samples collected daily for 20 days, were adjusted to pH 3-4 and extracted with ether. The aqueous portion containing conjugated metabolites was then subjected to acid hydrolysis and extracted with ether (Chadha and Madyastha 1984). Both the ether extracts were separated into neutral and acidic fractions. The total acidic fraction was methylated using diazomethane (Chadha and Madyastha 1984). Thin-layer chromatographic (TLC) analyses (silica gel G) of the metabolites were carried out using hexane-ethyl acetate. Separation and purification of the metabolites were accomplished by using a silica gel column and hexane-ethyl acetate as the eluent.
The acid methyl esters (250 mg) were subjected to TLC which showed the presence of one major compound i.e., methyl ester of 1,8-dihydroxy -10-carboxy p-methane and three minor compounds. The TLC analysis of the neutral fraction (200 mg) showed the presence of one major i.e., 2-hydroxy cineole and two minor metabolites. The neutral fraction (500 mg) obtained from hydrolysed urine on TLC analysis revealed the presence of two major (similar to 2-hydroxy cineole and 3-hydroxy cineole) and two minor metabolites. Based on the results, it is rather difficult to predict the sequence of reactions taking place during the biotransformation of cineole. However, one can envisage the formation of1,8-dihydroxy-10-carboxy-p-methane through the intermediary of p-methane 1,8-diol and further metabolism is possibly initiated by the oxygenation of the C-10 methyl group resulting in the formation of p-methane-1,8,10-triol which undergoes stepwise oxidation to the corresponding aldehydes and then to an acid. The opening of the ether bridge in cineole could result in the formation of a p-menthanoid cation with a positive charge either at C-1 or C-8 which further gets readily neutralized by the attack of a hydroxide ion to yield p- methane-1, 8-diol. The 2- and 3-hydroxy derivatives from cineole have been reported in bacterial (MacRae et al. 1979) and fungal systems (Nishimura et al. 1982) respectively. So it appears that the microbial systems are more specific while carrying out the hydroxylation of cineole unlike the mammalian system which hydroxylates at C-2 as well as C-3 position. Both these hydroxylated derivatives are excreted as conjugates.
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