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EC number: 259-952-2 | CAS number: 56038-13-2
- 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:
- 1983-09-20 to 1983-10-18
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 301 E (Ready biodegradability: Modified OECD Screening Test)
- Version / remarks:
- 1981
- Deviations:
- yes
- Remarks:
- inoculum quantity like OECD modified MITI test (guideline 301C (1981))
- GLP compliance:
- yes
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No. of test material: 153006
- Purity test date: 97.7%
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: at ambient temperature - Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge (adaptation not specified)
- Details on inoculum:
- - Source of activated sludge: activated sludge from a laboratory porous pot plant
- Preparation of inoculum for exposure: A sample of activated sludge was allowed to settle. The supernatant was discarded and the remaining sludge mixed thoroughly. A 25 mL sample was taken for determination of the concentration of suspended solids in order to calculate the volume required for addition to the test medium to obtain a final concentration of 30 mg suspended solids/L.
- Concentration of sludge: 30 mg suspended solids/L - Duration of test (contact time):
- 28 d
- Initial conc.:
- 4.5 mg/L
- Based on:
- DOC
- Parameter followed for biodegradation estimation:
- DOC removal
- Details on study design:
- TEST CONDITIONS
- Composition of medium: mineral nutrients in distilled water
- Test temperature: 20 - 25°C
- Suspended solids concentration: 30 mg/L
- Continuous darkness: yes
TEST SYSTEM
- Culturing apparatus: flasks, necks of flasks loosely covered with foil
- Number of culture flasks/concentration: 2
- Method used to create aerobic conditions: flasks were placed on a shaker
SAMPLING
- Sampling frequency: On day 0, 7, 14, 22 and 28
- Sampling method: Samples (50 mL) of each solution were taken and filtered through polycarbonate membranes of 0.2 µm pore size. The first 20 mL of filtrate was discarded and the remaining 30 mL was collected for duplicate determinations of DOC using a Carlo Erba total carbon monitor (400/P).
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes
- Other: reference with sodium benzoate - Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (DOC removal)
- Value:
- 4
- Sampling time:
- 28 d
- Results with reference substance:
- mean percentage removal of reference substance after 7 days = 92%
- Validity criteria fulfilled:
- not specified
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The biodegradation of the test substance was determined in a GLP study according to OECD 301 E. Within the test period of 28 days, a degradation of 4% was determined for the test substance. The test item was not significantly biodegraded under the conditions of this test.
Reference
sample | flask | Day 0 | Day 7 | Day 14 | Day 22 | Day 28 | |||||||||
DOC [mg/L] |
DOC corrected [mg/L] |
DOC [mg/L] |
DOC corrected [mg/L] |
removal [%] |
DOC [mg/L] |
DOC corrected [mg/L] |
removal [%] |
DOC [mg/L] |
DOC corrected [mg/L] |
removal [%] |
DOC [mg/L] |
DOC corrected [mg/L] |
removal [%] |
||
blank | mean | 1.8 | - | 2.7 | - | - | 3.15 | - | - | 4.95 | - | - | 1.55 | - | - |
reference | 3 | 21.0 | 19.2 | 4.6 | 1.9 | 90 | 3.8 | 0.5 | 97 | 5.1 | 0.2 | 99 | 1.7 | 0.2 | 99 |
4 | 21.6 | 19.8 | 3.6 | 0.9 | 95 | 3.5 | 0.4 | 98 | 4.5 | 0.0 | 100 | 1.6 | 0.1 | 99 | |
test | 5 | 12.5 | 10.7 | 14.2 | 11.5 | 0 | 12.3 | 9.2 | 14 | 22.9 | 18.0* | 0 | 11.8 | 10.3 | 3 |
6 | 12.8 | 11.0 | 15.7 | 13.0 | 0 | 12.9 | 9.8 | 11 | 21.0 | 16.1* | 0 | 12.0 | 10.5 | 5 |
* The unusually high values may be a result of an instrument error.
Description of key information
Based on the study results, the test substance can be considered for classification as not readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
The biodegradation of test item was determined in a GLP study according to OECD 301 E. The method is based on the removal of the dissolved organic carbon (DOC) of the test substance from a mineral medium inoculated with 30 mg activated sludge per L from a plant treating predominantly domestic sewage.Within the test period of 28 days, a degradation of 4% was determined for the test substance. A toxicity control was not included in the test.
Based on the study results and according to the criteria given in the ECHA Guidance (Guidance on the Application of the CLP Criteria) from 2015, the test substance can be considered for classification as not readily biodegradable.
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