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EC number: 200-864-0 | CAS number: 75-35-4
- 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:
1,1-dichloroethene is readily absorbed following inhalation or oral exposures. 1,1-dichlorethene can be metabolized by a system of mixed function oxidases (mainly CYP2E1). Excretion of 1,1-dichlorethene occurs via exhalation (as unchanged 1,1-dichloroethene or as CO2) or via feces or urine.
1,1-dichloroethene shows no bioaccumulation potential.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
1,1-dichloroethene is readily absorbed following inhalation or oral exposures. 1,1-dichlorethene can be metabolized by a system of mixed function oxidases (mainly CYP2E1). Excretion of 1,1-dichlorethene occurs via exhalation (as unchanged 1,1-dichloroethene or as CO2) or via feces or urine. 1,1-dichloroethene shows no bioaccumulation potential.
In vitro experiments on vinylidene chloride dermal absorption on human skin revealed that it can potentially be well absorbed by dermal route (Fasano et al., 2008).
Discussion on bioaccumulation potential result:
1,1-dichloroethene is readily absorbed following inhalation or oral exposures, and can be metabolized by system of mixed-function oxidases (mainly CYP2E1). With increasing doses of 1,1 -dichloroethene and subsequent saturation of the metabolizing enzymes, the proportion of 1,1 -dichloroethene exhaled unchanged increased markedly. Several pathways for metabolisation and excretion of 1,1-dichloroethene exist. Metabolisation occurs through the formation of an expoxide which can be further lead to the formation of CO2 which is excreted by exhalation or to the formation of non-volatile metabolites. The relative importance of these pathways depends on the dose, the route of administration, the absorption rate, the activity of the enzyme systems (species differences) and the body composition (fat content). When comparing the metabolizing systems from humans, rats and mice, those of mice showed most often the highest activity. Metabolites of 1,1 -dichloroethene can bind covalently to biomolecules and cause cellular damage in kidney, lung and liver which correlates with the high concentration of CYP2E1 in certain cell populations in these tissues. The main detoxification mechanism of reactive metabolites consists of glutathione conjugation. Therefore, exposure to high 1,1 -dichloroethene doses influences the glutathione concentration (in the liver) and the vice-versa the occurrence of adverse effects due to 1,1 -dichloroethene exposure is dependent on the glutathione levels. A conservative interpretation of a PBPK-model showed that
despite limitations due to extrapolation issues from rat to human, it can be reasonable assumed that the amount of epoxide formed from 1,1-dichloroethene is not higher in humans as compared to the rat at equivalent oral or inhalation concentrations.
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