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EC number: 204-662-3 | CAS number: 123-92-2
- 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
Generally, linear and branched-chain alkyl esters are hydrolysed to their component alcohols and carboxylic acids in the intestinal tract, blood and most tissues throughout the body (WHO, 1998).
Dahl et al. (1987):
The results indicated that esters, including potentially carcinogenic beta-lactones, are readily hydrolysed by respiratory tract enzymes; species and tissue differences were apparent (from the abstract of the publication). Furthermore, Dahl et al. (1987) stated: since rat maxilloturbinates typically contain 10 mg of S-9 [5], it is apparent that the rat maxilloturbinates alone have 10 times the necessary enzymatic capacity to completely hydrolyze phenyl acetate inhaled at 25 ppm.
In Dahl et al. (1987) was examined: Tissues from rats, rabbits and Syrian hamsters were investigated for carboxyl esterase activity. Tissues were: maxilloturbinates, ethmoturbinates, trachea, lung, liver. Substrates included esters of acetic acid with alcohols up to 8 carbon atoms and others: pentyl (amyl) acetate, methyl acetate, ethyl acetate, propyl acetate, butyl acetate, hexyl acetate, octyl acetate, iso-butyl acetate, sec-butyl acetate, tert-butyl acetate, phenyl acetate, beta-butyrolactone. The hydrolysis rate of structural isomers depended also on the branching of the alcohol: n-butyl acetate (77 nmol/mg S-9 protein/min) > iso-butyl acetate (67 nmol/mg S-9 protein/min) > sec-butyl acetate (62 nmol/mg S-9 protein/min) > tert-butyl acetate (42 nmol/mg S-9 protein/min).
Calculations carried out by Fiserova-Bergerova et al. (1990) indicate that exposure of 2% of the surface area of the body (360 cm2) to a saturated aqueous solution of 1-pentyl acetate increases the body burden by more than 30% but much less than 200% of the body burden resulting entirely from inhalation of a concentration of 100 ml/m3. It was thus predicted that the substance can be absorbed through the skin.
Key value for chemical safety assessment
- Bioaccumulation potential:
- low bioaccumulation potential
Additional information
The data from WHO (1998) and Dahl et al. (1987) suggest that isopentyl acetate (1 Mol) will be hydrolysed in the body to result in acetic acid (1 Mol) and 3-methyl-1-butanol (1 Mol).
The publication of Fiserova-Bergerova et al. (1990) suggest that pentyl acetates can be absorbed through the skin.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

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