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EC number: 208-235-2 | CAS number: 517-23-7
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 02.03. - 27.03.2001
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 E (Ready biodegradability: Modified OECD Screening Test)
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, domestic (adaptation not specified)
- Details on inoculum:
- The effluent of a sewage treatment plant treating predominantly municipal wastewater was used as incolum. The effluent came frome the drainage trench of the central sewage treatment plant of the city Neustadt (ESN), in the old stool, NW-Lachen-Speyerdorf. Sampling date: 19.02.2001, Lot number: 19022001.
- Pretreatment
The inoculum was kept aerobic during transport and storage. Before the test the batch was allowed to settle for one hour. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 40.2 mg/L
- Based on:
- DOC
- Parameter followed for biodegradation estimation:
- DOC removal
- Details on study design:
- The test was performed as a duplicate with calculated 40.2 mg/L carbon as starting concentration. The volume of each batch was 200 mL. Additionally, a reference approach with aniline was used, a control for abiotic degradation (poisoned batch without inoculum (with 10 ml of 1% HgCl2 solution)), a control for adsorption on bacteria (poisoned batch with inoculum) and as toxicity control a test with test substance and aniline.
0.5 mL effluent of sewage treatment plant/ L batch was added. The procedure for the blank control was the same, but without addition of test substance.
The procedure was carried out at 21 ± 2 ° C without direct illumination. The test duration was 28 days. (3 ± 0.5) h after the start of the test, at the end of the test as well at five intervening times (after 2, 5, 9, 14 and 20 days) 3.05 mL sample were taken from the incubation vessels for DOC measurement. The samples were filtered and the DOC content measured. - Reference substance:
- aniline
- Parameter:
- % degradation (DOC removal)
- Value:
- 88
- Sampling time:
- 28 d
- Results with reference substance:
- After 14 d 85% of the reference substance aniline were degraded. After 28 d a degradation of 95 % was found.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- The test item can be considered as readily biodegradable
- Executive summary:
The test item was tested for its ready biodegradability in the modified OECD screening test. The study procedure was based on OECD guideline No. 301 E, July 17, 1992.
The test was performed as a duplicate with calculated 40.2 mg/L carbon as starting concentration. The volume of each batch was 200 mL. Additionally, a reference approach with aniline was used, a control for abiotic degradation (poisoned batch without inoculum (with 10 ml of 1% HgCl2 solution)), a control for adsorption on bacteria (poisoned batch with inoculum) and as toxicity control a test with test substance and aniline. 0.5 mL effluent of sewage treatment plant/ L batch was added. The procedure for the blank control was the same, but without addition of test substance.
The procedure was carried out at 21 ± 2 ° C without direct illumination. The test duration was 28 days. (3 ± 0.5) h after the start of the test, at the end of the test as well at five intervening times (after 2, 5, 9, 14 and 20 days) 3.05 mL sample were taken from the incubation vessels for DOC measurement. The samples were filtered and the DOC content measured. The observed biodegradability was 88% after 28 days.
The criterion for ready biodegradability (at least 70% removal of DOC in a 10-day window) was also met in these experiment.
Thus, the substance was found to be readily biodegradable.
Reference
Description of key information
The test item was tested for its ready biodegradability in the modified OECD screening test. The study procedure was based on OECD guideline No. 301 E, July 17, 1992.
The test was performed as a duplicate. Additionally, a reference approach with aniline was used, a control for abiotic degradation (poisoned batch without inoculum (with 10 ml of 1% HgCl2 solution)), a control for adsorption on bacteria (poisoned batch with inoculum) and as toxicity control a test with test substance and aniline. 0.5 mL effluent of sewage treatment plant/ L batch was added. The procedure for the blank control was the same, but without addition of test substance.
The procedure was carried out at 21 ± 2 ° C without direct illumination. The test duration was 28 days. (3 ± 0.5) h after the start of the test, at the end of the test as well at five intervening times (after 2, 5, 9, 14 and 20 days) 3.05 mL sample were taken from the incubation vessels for DOC measurement. The observed biodegradability was 88% after 28 days.
The criterion for ready biodegradability (at least 70% removal of DOC in a 10-day window) was also met in these experiment.
Thus, the substance was found to be readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- freshwater
Additional information
A test on inherent biodegradation showed a degradation of 95 % after 23 d. Thus supporting the result of readily biodegradability of the test item.
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