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Diss Factsheets
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EC number: 231-959-5 | CAS number: 7782-50-5
- 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
Additional information
In natural water, the Cl2 molecule as well as hypochlorite ions are not stable due to the presence of organic and inorganic matter. The half-life of hypochlorite is estimated to be less than 2 hours due to reduction and photolysis. The freely available chlorine reacts to form various chlorinated by-products, e.g. chloramines and chloromethanes. In sewage, chlorine is mainly present in the form of chloramines, as hypochlorous acid undergoes a fast decay (SIAR, 2003).
In the atmosphere, chlorine mainly undergoes photolysis: Cl2 + hν => 2Cl°.
The half-lifetime for that process has been estimated to be in the order of 1–4 hours, depending on the time of the day (Hov, 1985; Peterson, 1976). Calculations show that half-lives for chlorine photolysis can range from less than 5 minutes to several hours, depending on the time of day, with representative values for latitudes 40°N and 55°N. The resulting chlorine atoms can then react with species present in the atmosphere such as ozone and saturated and unsaturated hydrocarbons. Recombination of chlorine after dissociation can be neglected due to the fast reaction with other species and due to the low concentration of chlorine. Chlorine atoms can also be produced by the reaction of hydrogen chloride with the hydroxyl radical (Hov, 1985). The reaction of chlorine with hydrocarbons gives rise to formation of chlorinated organic compounds (SIAR, 2003). However, on a global scale, the atmospheric burden of chlorine is dominated by natural rather than anthropogenic sources, and so anthropogenic sources will make only a very small contribution to these processes.
Mobility of chlorine in soil is assumed to be of little relevance as chlorine in an aqueous solution covalently binds to soil organics within the first few millimetres or centimetres of the soil surface. The final target compartment for chlorinated substances, formed from chlorine, will be the hydrosphere. Depending on the inherent properties and the stability of chlorinated products, chlorine may reside in the atmosphere. For example, NCl3 is highly volatile and is found in similar concentrations in air and water (SIAR, 2003).
An octanol/water distribution equilibrium can not be defined for chlorine as it has strong oxidizing properties and will react with the organic phase. A potential for bioaccumulation or bioconcentration of active chlorine species can be disregarded, because of their water solubility and their high reactivity (SIAR, 2003).
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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