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EC number: 701-219-0 | CAS number: 15174-47-7
- 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 – 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
No bioaccumulation potential expected based on several studies on cinnamaldehyde and cinnamyl derivatives. Studies indicate that cinnamyl derivatives can be anticipated to be rapidly absorbed, metabolized, and excreted, mainly in the urine, within 24 h.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
- Absorption rate - oral (%):
- 85
- Absorption rate - dermal (%):
- 85
- Absorption rate - inhalation (%):
- 100
Additional information
Alpha methyl-cinnamaldehyde is a cinnamyl derivative and as such has been extensively researched. Cinnamyl alcohol and related substances have been examined by the US FDA as part of the Food additives series research. The Committee evaluated a group of flavouring agents that included cinnamyl alcohol, cinnamaldehyde, cinnamic acid, and 52 structurally related substances. The evaluations were conducted according to the Procedure for the Safety Assessment of Flavouring Agents.
The position and size of the substituent play a role in the metabolism of cinnamyl derivatives. Those containing alpha-methyl substituents (e.g. alpha-methylcinnamaldehyde) are extensively metabolized via beta-oxidation and cleavage to yield mainly the corresponding hippuric acid derivative. A benzoic acid metabolite was isolated from the urine of dogs given either alpha-methylcinnamic acid or alpha-methylphenylpropionic acid (Kay & Raper, 1924). Larger substituents located at the alpha- or beta-position inhibited beta-oxidation to some extent (Deuel, 1957; Kassahun et al., 1991), in which case there may be direct conjugation of the carboxylic acid with glucuronic acid, followed by excretion. While alpha-methylcinnamic acid undergoes oxidation to benzoic acid, alpha-ethyl- and alpha-propylcinnamic acids are excreted unchanged (Carter, 1941). alpha-Ethylcinnamic alcohol and alpha-ethylcinnamaldehyde administered orally to rabbits resulted in urinary excretion of alpha-ethylcinnamic acid and of small amounts of benzoic acid (Fischer & Bielig, 1940). These observations suggest that alpha-methylcinnamaldehyde undergoes oxidation to benzoic acid, while higher homologues are excreted primarily unchanged or as the conjugated form of the cinnamic acid derivative.
In 5 reliable good quality studies (Nutley, 1990), (Sapienza et al., 1993), (Peters & Caldwell, 1994), (Caldwell & Nutley, 1986), (Nutley et al., 1994) it was showed that cinnamaldehyde, cinnamyl alcohol and cinnamic acid are all excreted via urine and faeces at 85 -98% within 24h and 90 -100% with 72h of oral ingestion.
Studies therefore indicate that cinnamyl derivatives such as alpha methylcinnamaldehyde can be anticipated to be rapidly absorbed, metabolized, and excreted, mainly in the urine, within 24h and totally excreted with 72h. There is therefore no bioaccumulation potential.
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