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EC number: 202-411-2 | CAS number: 95-33-0
- 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: inherent biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Principles of method if other than guideline:
- The ultimate degradation of the rubber chemicals to carbon dioxide was determined using the Monsanto shake flask procedure. The method is similar to ASTM draft method no. 2 ASTM Committee E35.24.
- GLP compliance:
- not specified
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- other: raw sewage, soil, and activated sludge mixture, acclimated
- Duration of test (contact time):
- 35 d
- Initial conc.:
- 20 mg/L
- Based on:
- test mat.
- Initial conc.:
- 30 mg/L
- Based on:
- test mat.
- Key result
- Parameter:
- % degradation (CO2 evolution)
- Value:
- ca. 0
- Sampling time:
- 35 d
- Interpretation of results:
- not inherently biodegradable
- Conclusions:
- No biodegradation of CBS was observed during 35 days of exposure to acclimated bacterial inoculum (Monsanto, 1979); and hence CBS can be concluded as not inherently biodegradable.
- Executive summary:
The inherent biodegradability of the test substance N-cyclohexxylbenzothiazole-2-sulphenamide was assessed in a study according the internal Monsanto shake flask method, which is similar to that deescribed in Draft Method No.2 for the proposed standard for the determination of the ultimate biodegradability of organic chemicals of the ASTM Committee E35.24 (1979). The substance was added to an inoculum of acclimated bacteria, which were previously mixed with a minimal salts media in a fluted 2-liter Erlenmeyer flask, after aerating the mixture with 70% oxygen in nitrogen. The Erlenmeyer flask was connected to a reservoir containing a 0.15 N barium hydroxide solution to trap evolving CO2 following biodegradation. The formation of CO2 was examined by titrating the barium hydroxide solution regularly.
For the test substance no biodegradation was observed during 35 days of exposure to acclimated bacterial inoculum (Monsanto, 1979); and hence N-cyclohexylbenzothiazole-2-sulphenamide can be concluded as not inherently biodegradable.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study without detailed documentation
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-F (Determination of the "Ready" Biodegradability - MITI Test)
- Version / remarks:
- Cited as Directive 84/449/EEC, C.7
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, predominantly domestic, non-adapted
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
- Reference substance:
- aniline
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 0
- Sampling time:
- 28 d
- Validity criteria fulfilled:
- yes
- Remarks:
- see 'Additional information'
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- For the test substance N-cyclohexylbenzothiazole-2-sulphenamide no biodegradation under test conditions was observed after 28 days in a guideline study according EU method C. 4.
- Executive summary:
In a MITI test according to EU method C. 4 the ready biodegradation of CBS was investigated (Bayer, 1989). After 28 days 0 % degradation of the test substance was determined and hence CBS under test conditions is not biodegradable.
Referenceopen allclose all
Method is similar in principle to Sturm test measuring ultimate biodegradation as CO2 evolved
71% aniline was biodegraded in 28 days according to oxygen consumption.
Description of key information
In a MITI test according to EU method C. 4 the ready biodegradation of CBS was investigated (Bayer, 1989). After 28 days 0 % degradation of the test substance was determined and hence CBS under test conditions is not biodegradable. Even with adapted bacterial inoculum CBS was observed to be 0% biodegradable during 35 days incubation (Monsanto, 1979). In the EU-risk assessment, information regarding the biodegardabilities of the main metabolites of CBS, such as MBT, MBTS, BT, BTon, MeSBT and MeBT, is also summarized and discussed. The described metabolites are also not readily biodegradable. Only when the inoculi were adapted under special conditions, certain level of degradation of MBT, BT, BTon, and MeSBT was observed. Such processes are expected in biological treatment plant, but not in the environment.
Key value for chemical safety assessment
- Biodegradation in water:
- not biodegradable
- Type of water:
- freshwater
Additional information
The concentrations (100 mg/l) used in the study of Bayer (1989) are much higher than the water solubility of CBS (i.e. 0.32 mg/l). Although CBS can be rather rapidly hydrolyzed with a half-life of 13.4 hours at 20 °C and pH 7 (Currenta 2022), the amount of CBS used was sufficient to maintain CBS at saturation level in aqueous phase. As the main hydrolysis products, benzothiazole (BT) and 2-mercaptobenzothiazole have a toxicity to microorganisms (3h-EC50) of 650 mg/l (Yo-shioka et al., 1986) and 3,301 mg/L (Bayer, 1990), respectively. The original concentrations from CBS are not high enough to reach the critical level of BT's toxicity to microorganisms, and hence no inhibition due to hydrolysis products is expected.
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