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EC number: 202-945-6 | CAS number: 101-48-4
- 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:
- 29 Jun - 27 Jul 1999
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-E (Determination of the "Ready" Biodegradability - Closed Bottle Test)
- Deviations:
- no
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: activated sludge from secondary effluent of a domestic sewage treatment plant (waste water treatment plant Odenthal, Germany); Date of collection: 25 Jun 1999
- Storage conditions: aerated
- Storage length: 4 d
- Pretreatment: separation of coarse particles by filtration
- Concentration of sludge: 5 mL/L (concentration of effluent in reaction mixture) - Duration of test (contact time):
- 28 d
- Initial conc.:
- 2.9 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Test temperature: 20 ± 1 °C
- Aeration of dilution water: yes
- Suspended solids concentration: 5 mL/L concentration of effluents in reaction mixture
- Continuous darkness: yes
TEST SYSTEM
- Number of culture flasks/concentration: 2
- Method used to create anaerobic conditions: the activated sludge was maintained in an aerobic condition by aeration for 4 h
SAMPLING
- Sampling frequency: 7, 14, 21, 28 days
- Sampling method: oxygen concentration was measured
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes, 2 bottles per sampling
- Toxicity control: yes, 2 bottles per sampling
- Other: Reference control: yes, 2 bottles per sampling
- Abiotic sterile control: no
- Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (O2 consumption)
- Value:
- 0
- Sampling time:
- 28 d
- Details on results:
- Within the test period of 28 days, a degradation of 0% was determined for the test item. Thus, the test item is not readily biodegradable according to the OECD criteria.
- Results with reference substance:
- The reference control achieved a degradation of 71% after 14 days.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The derived 28 d degradation rate was 0% for the test substance and 34% for the toxicity control. Since the test substance did not show any biodegradability within 28 d it is not considered to be readily biodegradable according to the OECD criteria. Due to the fact that the degradation rate of the toxicity control was > 25% after 14 d, toxic effects of the test substance to the inoculum can be excluded.
Reference
Biological Results:
Table 1: Results - DO depletion: % Degradation of test substance
Test substance Test concentration: 2.9 mg/L ThOD: 2409 mg/g COD : --- mg/g |
DO depletion after n days [mg/L] |
|||
7 d |
14 d |
21 d |
28 d |
|
No.1: (mt0 - mtx) - (mb0 - mbx) |
0.00 |
0.00 |
0.00 |
0.00 |
No.2: (mt0 - mtx) - (mb0 - mbx) |
0.00 |
0.00 |
0.00 |
0.00 |
Dl: % Degradation |
0 |
0 |
0 |
0 |
D2: % Degradation |
0 |
0 |
0 |
0 |
D, Mean |
0 |
0 |
0 |
0 |
Table 2: Results - DO depletion: % Degradation of the reference item
Reference substance Test concentration: 2.9 mg/1 ThOD: 1665 mg/g COD : --- mg/g |
DO depletion after n days [mg/L] |
|||
7 d |
14 d |
21 d |
28 d |
|
No.1: (mt0 - mtx) - (mb0 - mbx) |
3.30 |
3.40 |
3.69 |
3.71 |
No.2: (mt0 - mtx) - (mb0 - mbx) |
3.20 |
3.50 |
3.48 |
3.78 |
Dl: % Degradation |
68 |
70 |
76 |
77 |
D2: % Degradation |
66 |
72 |
72 |
78 |
D, Mean |
67 |
71 |
74 |
78 |
Table 3: Results - DO depletion: % Degradation of toxicity control
*Toxicity control |
DO depletion after n days [mg/L] |
|||
7 d |
14 d |
21 d |
28 d |
|
No.1: (mt0 - mtx) - (mb0 - mbx) |
3.14 |
3.57 |
4.10 |
3.94 |
No.2: (mt0 - mtx) - (mb0 - mbx) |
3.16 |
3.85 |
4.60 |
4.01 |
Dl: % Degradation |
27 |
30 |
35 |
33 |
D2: % Degradation |
27 |
33 |
39 |
34 |
D, Mean |
27 |
32 |
37 |
34 |
* In the toxicity control 2.9 mg/L test substance and 2.9 mg/L reference substance were used. The ThOD values respectively COD values of these substances are shown in the tables above.
Description of key information
Not readily biodegradable: 0% within 28 d (OECD 301D)
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
One GLP guideline study according to OECD 301D is available investigating the ready biodegradability of the substance. A mixed microbial population of the activated sludge of a local municipal STP was inoculated with a nominal concentration of 2.9 mg/L test substance and incubated for 28 d under controlled conditions in the dark. Degradation was followed by the determination of dissolved oxygen content after 0 h, 7, 14, 21 and 28 d. An inoculum blank, a reference control and a toxicity control were run in parallel. The derived 28 d degradation rate was 0% for the test substance and 34% for the toxicity control. Since the test substance did not show any biodegradability within 28 d it is not considered to be readily biodegradable according to the OECD criteria. Due to the fact that the degradation rate of the toxicity control was >25% after 14 d, toxic effects of the test substance to the inoculum can be excluded.
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