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EC number: 212-222-7 | CAS number: 770-35-4
- 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
Short description of key information on bioaccumulation potential result:
A GLP-study on metabolism of PPh in rats after oral administration is available for phenoxypropanol
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
Based on the results of a study in male rats, PPh is rapidly absorbed, distributed, and quickly metabolized and eliminated. Virtually all the administered dose is eliminated within 48 hours in the urine and feces. The three major routes of metabolism are 1) cleavage of PPh by O-dealkylation, yielding propylene glycol and phenol, followed by excretion of phenol as a sulfate, or glutathione conjugate in the urine; 2) direct sulfate or glucuronide conjugation of parent PPh and excretion into the urine; and 3) ring hydroxylation of parent PPh or its oxidized propanone metabolite, followed by sulfate conjugation and excretion into the urine. Minor urinary metabolites included the glucuronide conjugate of hydroquinone. PPh is rapidly absorbed, distributed throughout the body, and eliminated, similar to other propylene glycol ethers (PGEs). The major routes of elimination, urine and feces, also are similar to other PGEs. The types of metabolites, parent ether conjugates, hydrolyzed propylene glycol, and hydrolyzed alcohol (phenol) conjugates, also are similar.
Discussion on bioaccumulation potential result:
Adult, male F344 rats were administered a single oral dose of 10 or 100 mg/kg radiolabeled DOWANOL PPh. The major route of elimination of DOWANOL PPh was through urine, accounting for 88 ± 12% of the low and 96 ± 3% of the high dose. Most of the urinary excretion of DOWANOL PPh derived radioactivity occurred within 12 hr after dosing; 81 ± 9% of the low and 90 ± 1% of the high dose. Total fecal elimination remained < 10% during the course of the study. Rats eliminated the entire administered dose within 48 hr after dosing, with total recovery ranging from 100 – 106%. Metabolites tentatively identified in urine were conjugates of phenol (sulfate, glutathione), as well as conjugates of parent compound (glucuronide, sulfate) and a ring-hydroxylated metabolite of parent. There was no free parent compound or phenol detected in non-acid-hydrolyzed urine. In acidhydrolyzed urine, 61% of the dose was identified as phenol and 13% as DOWANOL PPh. Although the parent compound was stable to acid hydrolysis, some of the phenol in acid hydrolyzed urine may have come from degradation of acid-labile metabolite(s) as well as hydrolysis of phenol conjugates.
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