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Diss Factsheets
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EC number: 200-431-6 | CAS number: 59-50-7
- 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
Hydrolysis:
The hydrolysis of chlorocresol was estimated to be 0.0000000000256787 cm3/molecule - seconds. The estimated half life of the substance indicates that the substance is non persistent in nature as the OH rate constant is negligible and so the substance is biodegradable.
Biodegradation in water: screening tests:
According to the PBT profiler model, Chlorocresol degrades 50% in water in 38 days, suggesting that it is readily biodegradable in water and it will not be persistent in the aquatic environment
Media |
Half-Life |
Percent in |
water
|
38 |
19% |
Biodegradation in water and sediment: simulation tests:
Chlorocresol degrades 50% in water in 37.5 days, suggesting that it is readily biodegradable in water. However, in the sediment Chlorocresol has a long half life of 337.5 days. Thus it can be concluded that Chlorocresol will be persistent in the sediment given its long half life of 337.5 days.
Media |
Half-Life |
Percent in |
Water |
37.5 |
19.1% |
Sediment |
337.5 |
0.519% |
Biodegradation in soil:
Half-life of chlorocresol in soil was estimated to be 1800 hours i.e. 75 days .Thus is can be concluded that chlorocresol is persistent in soil given the half life of 75 days which is slightly greater than the threshold of 60 days (half life) indicating ready bio-degradability and low persistence in soil
Media |
Half-Life |
Percent in |
Soil
|
75 |
80% |
Bioaccumulation: aquatic / sediment:
BCF values of 5.5 to 11 and 6.7 to 13 were measured using initialChlorocresolconcentrations of 2 ug/l and 20 ug/l, respectively. Tests were conducted in a continuous flow system with six weeks exposure using carp having an average lipid content of 4.9 percent. According to a classification scheme, these BCF ranges suggest the potential for Bioconcentration in aquatic organisms is low (SRC). For the purpose of chemical safety assessment and dossier preparation, Bioconcentration factor of 11 has been considered.
Adsorption / desorption:
The Koc of chlorocresol was found to be 490. According to a classification scheme, this Koc value suggests that chlorocresol is expected to have moderate mobility in soil. In addition, this chemical was found to be mobile in an activated carbon-sand filter system; this was considered to be indicative of a low adsorption potential in soil systems.
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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