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Diss Factsheets
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EC number: 200-879-2 | CAS number: 75-56-9
- 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
There are extensive data available from animal models and in vitrowork on the toxicokinetics of propylene oxide that indicate that about 25% of inhaled propylene oxide is absorbed(Csanádyand Filser, 2006; Morris et al., 2004; Morris and Pottenger, 2006).
Two studies investigated upper respiratory uptake of propylene oxide in rats and mice. Rats were exposed to 300 ppm propylene oxide for 15, 30, 45, or 60 min at a flow rate of 200 ml/min or 50 ml/min (Morris et al., 2004). The uptake average was approximately 25% efficient at 50 ml/min flow rate compared to approximately 11% efficient at 200 ml/min flow rate, regardless of the exposure concentration. In this study at concentrations of 100 ppm or more, propylene oxide exposure resulted in significant depletion of nasal respiratory mucosal nonprotein sulfhydryls (NPSH), providing strong evidence that direct reaction and/or conjugation of propylene oxide with glutathione and/or other NPSH groups occurred. Propylene oxide exposure was shown to also deplete nasal NPSH levels in the mouse. Olfactory NPSH content averaged 63 and 48% of control in the 300- and 500-ppm groups. (Morris and Pottenger, 2006). Average uptake was similar to that observed in rats with 29% efficient at 12 ml/min flow rate and approximately 11% efficient at 50 ml/min flow rate, regardless of the exposure concentration.
Propylene oxide is demonstrated to berapidly biotransformed by rats. Only a small fraction (3%) was exhaled unchanged (Golkaet al., 1989); the majority of absorbed propylene oxideis widely distributed throughout the organism following inhalation exposure to high levels, based on adduct formation in proximal and distant tissues (Osterman-Golkar et al., 2003; Rios-Blancos et al., 1997, 2000, 2003). The absorbed propylene oxide is available for detoxificationviaglutathione-S-transferase-mediated conjugation with glutathione (GSH) or hydrolysisviaEpoxide Hydratase (EH) (Faller et al., 2001; Lee et al, 2005). Propylene oxide also binds with cellular macromolecules, including hemoglobin and DNA (Osterman-Golkar et al., 1999, 2003; Rios-Blancos et al., 1997, 2000, 2002, 2003). Such data provide important dosimetry information on the internal dose and distribution of propylene oxide, including calculation of the half-life of 3 days for the predominant DNA adduct formed, the N7-hydroxypropylguanine (Segerback et al., 1994, 1998; Plna et al., 1999).
The limited data available from worker populations (Boogaardet al., 1999;Czèneet al., 2002; Schettgenet al., 2002) indicate that propylene oxide is absorbed and that adduct formation occurs in humans exposedviainhalation, similar to the animal data.
Based on the information available, propylene oxide is expected to be readily absorbed through the gastrointestinal and respiratory tracts and widely distributed to the major organs. There is no data available for dermal absorption but acute dermal toxicity data indicate the potential for dermal absorption of the liquid. No information is available regarding the potential for dermal absorption of the vapour.
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.
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