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EC number: 224-167-6 | CAS number: 4221-98-1
- 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
Based on physicochemical characteristics, particularly water solubility and octanol-water partition coefficient, absorption by the oral and dermal route may take place to a small extend. This assumption is supported by the results of the oral and dermal acute toxicity studies, revealing some effects only at very high doses, as well as the combined repeated dose oral toxicity study with the reproduction/developmental screening test. Absorption via inhalation may also take place. Bioaccumulation of alpha phellandrene products cannot be excluded based on the available data. After metabolisation, the substance will be mainly excreted via urine.
Key value for chemical safety assessment
Additional information
The test substance is a colourless to pale yellow clear liquid at room temperature with a molecular weight of136.234 g/mol.The substance has a water solubility of 4.37 mg/L at 20 °C. The log Pow of alpha phellandrene was determined to be 5.74. The substance has a vapour pressure of 2.35 hPa at 20 °C.
Absorption
Generally, oral absorption is favoured for molecular weights below 500 g/mol. The water solubility of the substance is too low to allow the substance to readily dissolve in the gastrointestinal fluids, allowing direct uptake into the systemic circulation through aqueous pores or via carriage of the molecules across membranes with the bulk passage of water. But, as alpha phellandrene has a water solubility of 4.37 mg/L together with a log Pow value >4, it may be taken up by micellular solubilisation. As mortality was observed in the acute oral toxicity study at higher doses, the substance was proven to be taken up by oral route. Besides that, the effects observed in the OECD 422 study (test substance-related changes in the liver in males of the 75 mg/kg bw/d dose group and in males and females of the 200 mg/kg bw/ d dose group, increased liver weights in both sexes at 75 and 200 mg/kg bw/d) also serve as a proof of uptake via the oral route.
No experimental data for exposure following the respiratory route are available. Due to the vapour pressure of 2.35 hPa (at 20 °C) of the substance, it may become available as a vapour. Absorption via inhalation route is considered possible as absorption via oral route does also take place.
Dermal uptake is favoured for substances with a molecular weight <100 g/mol, but possible for substances with a molecular weight <500 g/mol. The log Pow of alpha phellandrene is >5 and therefore the rate of penetration may be limited by the rate of transfer between the stratum corneum and the epidermis, but uptake into the stratum corneum will be high. Dermal absorption cannot be excluded, but is not assumed to take place at high rates. The acute dermal toxicity study did not reveal any systemic effects. Signs of slight (reversible) irritation were noted in the animals, indicating skin damage that may enable penetration at low rates. In addition the substance was shown to be sensitising to skin, thus proving dermal uptake must have occurred, at least to a low extend.
Distribution
As mentioned above, the physicochemical properties of alpha phellandrene allow systemic absorption following oral and dermal uptake.
In general, the smaller the molecule the wider the distribution. The results of the OECD 422 study show that the substance must reach the liver, as there were reversible histopathologically findings in males of the 75 mg/kg bw/d dose group and in males and females of the 200 mg/kg bw/ d dose group (centrilobular hepatocellular hypertrophy) as well as increased liver weights in both sexes at 75 and 200 mg/kg bw/d. Taken into account its log Pow and the water solubility, accumulation of alpha phellandrene cannot be excluded. The calculated BCF value of 2846 L/kg does further imply a bioconcentration potential of the substance. The available study data revealed no indications of the substance to cross the blood-brain barrier.
Metabolism
Metabolism mainly occurs in liver especially following oral intake.
From thein vitrogenotoxicity studies no remarkable differences in regard to genotoxicity and cytotoxicity in the presence or absence of metabolic S9-mix could be detected, therefore not indicating metabolism to more toxic compounds inin vitroand probably alsoin vivo.
Due to its chemical structure the substance might probably be converted to more polar products via phase I oxidation reactions at the methyl side chain or at the isopropyl side chain. Further conjugation reactions (phase II) may also occur.
Besides that reactions taking place at the ring structure are possible as predicted by the OECD QSAR-Toolbox metabolism simulators (in vivo rat metabolism simulator, rat liver S9 mix simulator and skin metabolism simulator). The double-bonds of the ring structure are attacked resulting in epoxidation and further hydrolysation of the epoxide. Ring opening reactions are also possible.
Due to the enhanced hydrophilicity of the metabolisation products elimination via urine can take place.
Excretion
The metabolites of alpha phellandrene are most likely excreted via urine due to their small molecular weight and their enhanced water solubility.
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