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Diss Factsheets
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EC number: 500-057-6 | CAS number: 27104-30-9
- 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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
Description of key information
The key study carried according to OECD Guideline provides a 3h-EC50 value of 74 mg/L.
Key value for chemical safety assessment
- EC50 for microorganisms:
- 74 mg/L
Additional information
Two experimental studies (first in 1992; second in 1994) reported results of acute toxicity tests of the mixture of the registered substance in water to bacteria from activated sludge. Both studies were performed according to OECD Guideline No 209 (1984). A 3 -hour range-finding test and a 3 -hour definitive test were carried out in the study performed in1994. A 30 -minute definitive test and a 3 -hour definitive test were carried without range-finding test of the first experiment (1992). Inoculums were sampled from the same location namely the aeration stage of Severn Trent Water PLC sewage Treatment Plant.
Validity criteria
In both studies, the 3h-EC50 value for the positive control (3,5-dichlorophenol) was found in the range 5-30 mg/L which is one validity requirement from the OECD Guideline No 209.
In the definitive test from 1994, the respiration rates from the two controls differ from each other of 18%. This value, being higher than 15%, is a deviation from the OECD Guideline No 209. In addition, no dose-response relationship was depicted by the author. The range-finding test provides a 3h-EC50 value of 260 mg/L (based on nominal concentration).
In both tests performed in 1992, the requirements of the control respiration rate were fulfilled.
Inconsistency of results
One inconsistent result was observed between the range-finding test and the definitive from the first experiment (1992): at 100 mg/L, the percentage of inhibition was 20% whereas no inhibition was observed in the main test.
Conclusion
Following the review of both study reports, the second test (1994) was qualified as reliable with restrictions (2) and the first study (1992) as reliable without restrictions. Then the study in 1992 was flagged as key study for this endpoint with EC50 -3h=74 mg/L.
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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