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EC number: 200-870-3 | CAS number: 75-44-5
- 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
Description of key information
Phosgene is very toxic by inhalation.
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LC50
- Value:
- 8.6 mg/m³
- Quality of whole database:
- The study is GLP compliant and of high quality (Klimisch score=1)
Acute toxicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
No animal studies on acute oral or dermal toxicity of phosgene are available. Since phosgene is a gas at room temperature and phosgene in aqueous environment rapidly hydrolyses to carbon dioxide and hydrochloric acid, exposure by the oral or dermal route is highly unlikely. The half-life in water has been estimated at 0.026 seconds (Manogue and Pigford , A.I.Ch.E. Journal 6(3): 494-500 (1960)).
An acute inhalation toxicity test in rats with phosgene gas (nose-only) according to OECD TG 403 revealed median lethal concentrations (LC50) and estimated non-lethal threshold concentrations (LC01) for 10, 30, 60 and 240 minutes of 253.3 (105.3), 54.5 (29.2), 31.3 (21.1), and 8.6 (5.3) mg/m3, respectively (Pauluhn, 2006a). The corresponding Cn x t products were 2532, 1635, 1878, and 2052 mg/m3 x min. In this range of exposure durations, the exponent n was found to be ≈ 0.9 for both median lethal (LC50) as well as the lethal threshold (LC01) effects. The ratios of LC50/LC01 were 2.4, 1.9, 1.5, and 1.6 for 10, 30, 60, and 240 minutes, respectively. Due to the apparent rat-specific changes in breathing patterns at very short durations of exposure, a generic ratio of 1.5 appears to be most representative. In all exposure groups of both sexes clinical signs of the respiratory tract (mainly bradypnea, labored breathing patterns, irregular breathing patterns, stridor, breathing sounds, nasal discharge (serous) and salivation) were observed after phosgene exposure. Statistically significant and concentration-dependent effects of body weight gains were observed in all exposure groups. In all rats that succumbed during the course of study an increased incidence of macroscopic alterations of the respiratory tract were found. These were characterized by a white foamy discharge from the nose, a less collapsed and discolorated (mainly dark-red) lung, hydrothorax, and trachea with white foamy content. Surviving rats did not show macroscopic alterations considered to be of pathodiagnostic significance. In summary, the inhalation LC50 in rats of both sexes was determined to be 8.6 mg/m3 for 4 hours of exposure to phosgene gas. The analysis of the C × t dependent mortality revealed a steep C × t mortality relationship. The various C x t products appear to follow Haber's rule, although departures may occur at high-level short-term exposures due to apparent rodent-specific irritant related changes in breathing patterns.
In a further acute inhalation study in male rats LC0 values of 15.36 and 1.57 mg/m3 were determined after 30- and 240 min exposure (nose-only) to phosgene gas (Pauluhn, 2006b). The corresponding C x t products of 461 (30 min) and 376 (240 min) mg/m3 x min provided evidence of a transient impairment of the alveolar blood-air barrier; however, which did not lead to any long-term changes of lung tissue.
In an acute inhalation study in male and female Beagle dogs no animal died after a single 30 min exposure (head-only) to 35 mg/m3 phosgene gas (Pauluhn, 2006c). At this test concentration an intraalveolar edema with some evidence of an adversely affected gas exchange was observed. The corresponding C x t product was 1050 mg/m3 x min.
For evaluation of acute inhalation toxicity see also chapter 7.9.3 "Endpoint summary: Mechanism of action (inhalation toxicity)" where the outcome of the acute toxicity studies in rats (Pauluhn, 2006b) and dogs (Pauluhn, 2006c) were discussed with regard to the derivation of an occupational exposure limit (MAK value; EU SCOEL).
Justification for selection of acute toxicity – inhalation endpoint
Only one key study with a 4h LC50 value available
Justification for classification or non-classification
Classified according to Annex I of Directive 67/548/EEC with R26 (very toxic by inhalation) and according to Annex VI of Regulation (EC) No 1272/2008 with Acute Tox Cat.1 (H330: Fatal if inhaled).
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