Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vitro / ex vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Acceptable, well-documented study report, which meets scientific principles
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 007
Materials and methods
- Objective of study:
- toxicokinetics
- Principles of method if other than guideline:
- Kinetic study of acidic hydrolysis of CBS at pH 1 at 35°C
- GLP compliance:
- no
Test material
- Reference substance name:
- N-cyclohexylbenzothiazole-2-sulfenamide
- EC Number:
- 202-411-2
- EC Name:
- N-cyclohexylbenzothiazole-2-sulfenamide
- Cas Number:
- 95-33-0
- Molecular formula:
- C13H16N2S2
- IUPAC Name:
- N-(1,3-benzothiazol-2-ylsulfanyl)cyclohexanamine
- Details on test material:
- CBS commercial grade, active matter content: 97.7%
Constituent 1
Test animals
- Species:
- other: in vitro
Results and discussion
Main ADME resultsopen allclose all
- Type:
- other: Acidic hydrolysis of CBS
- Results:
- CBS is metabolised to MBTS in a two-step reaction
- Type:
- other: Acidic hydrolysis of CBS
- Results:
- acid hydrolysis of CBS at pH 1 is nearly constant 9% per day for the first 6 to 7 days, rapid drop down to 2% per day for the following time
Any other information on results incl. tables
Within the first 6.5 days (=156 h) the rate of hydrolysis is nearly linear with about 9.0% over day based on the CBS amount at t = 0h and than drops to about 2.0% for the following 9.5 days (= 228 h). Parallel to this pH increase per day within the first 6.5 days is about 0.4 and than suddenly drops to about 0 for the following days.
A correlation of the CBS loss with the formation of MBTS shows that at the beginning the rate of hydrolysis is remarkably higher than the rate of MBTS formation which easily be explained with the low MBT concentration in this period. When there is enough MBT present, which at pH<5 is a precipitated solid like CBS and MBTS, the MBTS formation rate increases rapidly to slow down again after 8 to 9 days (= 216 h) to nearly the same rate than that of the CBS hydrolysis. The trend of the sums of the MBT moieties of CBS and MBTS shows that within analytical accuracy all hydrolyzed CBS is metabolized to MBTS in two steps; in the beginning free mercaptobenzothiazole (MBT) and cyclohexylamine appeared. The free MBT then reacted directly with the starting substance CBS leading to dimeric MBT (mercaptobenzothiazyl disulfide, MBTS) and cyclohexylamine. The interim formed MBT was not measured as it is dissolved during work-up of the sample.
Applicant's summary and conclusion
- Executive summary:
Within the first 6.5 days (=156 h) the rate of hydrolysis is nearly linear with about 9.0% over day based on the CBS amount at t = 0h and than drops to about 2.0% for the following 9.5 days (= 228 h). Parallel to this pH increase per day within the first 6.5 days is about 0.4 and than suddenly drops to about 0 for the following days.
A correlation of the CBS loss with the formation of MBTS shows that at the beginning the rate of hydrolysis is remarkably higher than the rate of MBTS formation which easily be explained with the low MBT concentration in this period. When there is enough MBT present, which at pH<5 is a precipitated solid like CBS and MBTS, the MBTS formation rate increases rapidly to slow down again after 8 to 9 days (= 216 h) to nearly the same rate than that of the CBS hydrolysis. The trend of the sums of the MBT moieties of CBS and MBTS shows that within analytical accuracy all hydrolyzed CBS is metabolized to MBTS in two steps; in the beginning free mercaptobenzothiazole (MBT) and cyclohexylamine appeared. The free MBT then reacted directly with the starting substance CBS leading to dimeric MBT (mercaptobenzothiazyl disulfide, MBTS) and cyclohexylamine. The interim formed MBT was not measured as it is dissolved during work-up of the sample.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.