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Diss Factsheets
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EC number: 206-190-3 | CAS number: 306-83-2
- 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
Exposure related observations in humans: other data
Administrative data
- Endpoint:
- exposure-related observations in humans: other data
- Type of information:
- other:
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
Data source
Reference
- Reference Type:
- publication
- Title:
- Hepatotoxicity Associated with Overexposure to 1,1-Dichloro-2,2,2-Trifluoroethane (HCFC-123)
- Author:
- Boucher R, Hanna C, Rusch GM, Stidham D, Swan E, Vazquez M
- Year:
- 2 003
- Bibliographic source:
- Am. Ind. Hyg. Ass. J. 64, 68-79
Materials and methods
Results and discussion
Applicant's summary and conclusion
- Executive summary:
8 workers exposed to HCFC-123 used as a precision cleaning agent showed marked elevations in ALT and AST after 1-4 months of exposure. The analysis of working conditions showed that 2 workers presenting liver alterations could have experienced intermittent high exposures. However, other affected workers were not operating directly with the degreaser system. Industrial hygiene sampling collected during the start-up period after introduction of HCFC-123 indicated personal samples ranging from 24-480 ppm for 375 and 21 minutes, respectively. No exposure determination was available during the time when the liver abnormalities were suspected to have developed; however, personal and area sampling collected after the finding revealed concentrations of 5-12 ppm HCFC-123. The exposure occurred prior to the finding of liver abnormality was estimated theoretically by means of 2 different models, one considering the workplace as a homogeneous box and another considering the plant divided into 2 smaller areas. In the first model a conservative estimate of air change rate 6 changes/day was assumed, whereas 12 or 28 air changes/day were considered in the second model. The first conservative simulation gave an estimated 8-h TWA concentration ranging from 10 to 35 ppm. The second model indicated that workers operating closely to the degreaser could have been exposed to daily peak concentrations ranging from 280 to 2,100 ppm and respective 8-h TWA concentrations of 252-1,630 ppm, whereas workers not working around the degreaser could have experienced peak exposures of 28-210 ppm and 8-h TWA of 25-163 ppm (Boucher et al., 2003)
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