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EC number: 248-370-4 | CAS number: 27253-29-8
- 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
Key value for chemical safety assessment
Additional information
Due to the stability conferred by the quaternary carbon, neoacids are relatively resistant to biotransformation and do not readily form bioactive metabolites. Enzymatic removal of the alkyl groups at the quaternary carbon allows for other metabolic processes to occur; mitochondrial beta-oxidation or by cytochrome P450 mediated omega and omega-minus-one oxidation (may be followed by beta-oxidation) to produce acetate. However, since neoacids are not readily metabolized, they are primarily eliminated in the urine as glucuronic acid conjugates, carnitine conjugates or after dealkylation (Brass, 2002).
Studies in Animals
Test data exist on three representative neoacids: C5, C7, and C10. In pharmacokinetic studies, C5 was absorbed via oral and dermal routes of exposure. In an in vitro study using porcine skin, the permeability constant (Kp × 103) of C5 was 0.2 cm/min. In comparison, the permeability constant (Kp × 103) of other acids was 1.0 cm/min for C4 (butyric) and 0.31 cm/min for C5 (methyl butyric) (Liron and Cohen, 1984). There is no evidence of marked tissue accumulation of neoacids. Excretion pathways include urine and feces.
In a study with C10, rats were fed 100 mg/kg/day of neodecanoic acid for 5 days and followed by a pulse of C-14 labelled neodecanoic acid and assessed every 24 hours for 3 days to determine the distribution and excretion. It was found that under the conditions of the experiment, 70-80% of the administered activity could be accounted for. Excretion in the urine may expect to range from 50-60% while that in the feces will vary from 40-50%. In any case, the total of these two will be at least 98%. The excretion rate falls off rapidly such that less than 1% of dose is expected past 72 hours. Expired air reaches a peak rate somewhere around 12 hours or earlier. The total carcass, exclusive of organs, retains less than 1% of the recovered dose. Intestines had the greatest specific activity and contribute as much as 1% of total dose. Analysis by thin layer chromatography shows that the bulk of excreted activity is either the original free acid or a material which is readily converted to the acid upon mild hydrolysis.
Limited data suggest that metabolism will vary depending on the neoacid. In rodents and monkeys, C5 does not undergo appreciable metabolism but can form conjugated products which will facilitate excretion from the body (Brass, 2002; Vickers et al., 1985). The C10 neoacid can also form glucuronides that are rapidly eliminated from the body (ExxonMobil, 1968).
Studies in Humans
Data exits on neoacid C5 (pivalic acid). Human studies demonstrated the formation of pivaloyl carnitine and urinary pivaloyl carnitine excretion as the main route of C5 elimination (Brass, 2002; Vickers et al., 1985).
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