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EC number: 213-424-8 | CAS number: 947-04-6
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
Description of key information
Methods for the determination of effects of chemicals on organisms arising from atmospheric contamination have not yet been developed, except for inhalation studies with mammals. Therefore, a hazard assessment and in consequence the risk characterisation of chemicals in air cannot be applied. The inhalative uptake of the substance by humans is considered by the assessment of exposure of humans via the environment.
Biodegradation in water was determined in a Modified Storm Test (CO2 Evolutio
Biodegradation in water was determined in a Modified Storm Test (CO2 Evolution Test) by Infracor GmbH (2002) according to the EU method C4 and OECD 301 B. The study was conducted with activated sludge obtained from a municipal WTP. CO2 evolution was quantified via measurement of dissolved organic carbon using a Carbon analyser.
83% degradation were observed within a period of 28 days. As >60% biodegradability were observed within the 10d-window the test item can be assessed as readily biodegradable.
Due to the ready biodegradability further degradation tests in water, sediment and soil are not necessary according to column 2 of Annex IX of REACH Regulation1907/2006.
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Biodegradation in water was determined in a Modified Storm Test (CO2 Evolution Test) by Infracor GmbH (2002) according to the EU method C4 and OECD 301 B. The study was conducted with activated sludge obtained from a municipal WTP. CO2 evolution was quantified via measurement of dissolved organic carbon using a Carbon
83% degradation were observed within a period of 28 days. As >60% biodegradability were observed within the 10d-window the test item can be assessed as readily biodegradable.
Due to the ready biodegradability further degradation tests in water, sediment and soil are not necessary according to column 2 of Annex IX of REACH Regulation1907/2006.
Biodegradation in water was determined in a Modified Storm Test (CO2 Evolution Test) by Infracor GmbH (2002) according to the EU method C4 and OECD 301 B. The study was conducted with activated sludge obtained from a municipal WTP. CO2 evolution was quantified via measurement of dissolved organic carbon using a Carbon analyser.
83% degradation were observed within a period of 28 days. As >60% biodegradability were observed within the 10d-window the test item can be assessed as readily biodegradable.
Due to the ready biodegradability further degradation tests in water, sediment and soil are not necessary according to column 2 of Annex IX of REACH Regulation1907/2006.
Biodegradation in water was determined in a Modified Storm Test (CO2 Evolution Test) by Infracor GmbH (2002) according to the EU method C4 and OECD 301 B. The study was conducted with activated sludge obtained from a municipal WTP. CO2 evolution was quantified via measurement of dissolved organic carbon using a Carbon analyser.
83% degradation were observed within a period of 28 days. As >60% biodegradability were observed within the 10d-window the test item can be assessed as readily biodegradable.
Due to the ready biodegradability further degradation tests in water, sediment and soil are not necessary according to column 2 of Annex IX of REACH Regulation1907/2006.
Biodegradation in water was determined in a Modified Storm Test (CO2 Evolution Test) by Infracor GmbH (2002) according to the EU method C4 and OECD 301 B. The study was conducted with activated sludge obtained from a municipal WTP. CO2 evolution was quantified via measurement of dissolved organic carbon using a Carbon analyser.
Biodegradation in water was determined in a Modified Storm Test (CO2 Evolution Test) by Infracor GmbH (2002) according to the EU method C4 and OECD 301 B. The study was conducted with activated sludge obtained from a municipal WTP. CO2 evolution was quantified via measurement of dissolved organic carbon using a Carbon analyser.
83% degradation were observed within a period of 28 days. As >60% biodegradability were observed within the 10d-window the test item can be assessed as readily biodegradable.
Due to the ready biodegradability further degradation tests in water, sediment and soil are not necessary according to column 2 of Annex IX of REACH Regulation1907/2006.
83% degradation were observed within a period of 28 days. As >60% biodegradability were observed within the 10d-window the test item can be assessed as readily biodegradable.
Due to the ready biodegradability further degradation tests in water, sediment and soil are not necessary according to column 2 of Annex IX of REACH Regulation1907/2006.
The test item proved to be ready biodegradable in the "Modified Sturm Test" according to OECD 301 B. 83% degradation were observed with in a period of 28 days. The study was assessed as "reliable without restrictions".
The test item proved to be ready biodegradable in the "Modified Sturm Test" according to OECD 301 B. 83% degradation were observed with in a period of 28 days. The study was assessed as "reliable without restrins".
Methods for the determination of effects of chemicals on organisms arising from atmospheric contamination have not yet been developed, except for inhalation studies with mammals. Therefore, a hazard assessment and in consequence the risk characterisation of chemicals in air cannot be applied. The inhalative uptake of the substance by humans is considered by the assessment of exposure of humans via the environment.
The test item proved to be ready biodegradable in the "Modified Sturm Test" according to OECD 301 B. 83% degradation were observed wi
The test item proved to be ready biodegradable in the "Modified Sturm Test" according to OECD 301 B. 83% degradation were observed with in a period of 28 days.
and OECD 301 B. The study was conducted with activated sludge obtained from a municipal WTP. CO2 evolution was quantified via measurement of dissolved organic carbon using a Carbon analyser.
Since more than 60% biodegradability were observed within the 10d-window the test item is assessed as readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
Biodegradation in water was determined in a Modified Storm Test (CO2 Evolution Test) by Infracor GmbH (2002) according to the EU method C4 and OECD 301 B. The study was conducted with activated sludge obtained from a municipal WTP. CO2 evolution was quantified via measurement of dissolved organic carbon using a Carbon analyser.
83% degradation were observed within a period of 28 days. As >60% biodegradability were observed within the 10d-window the test item can be assessed as readily biodegradable.
Due to the ready biodegradability further degradation tests in water, sediment and soil are not necessary according to column 2 of Annex IX of REACH Regulation1907/2006.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.