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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 273-227-8 | CAS number: 68953-84-4
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Although no guideline is followed, the study design is clearly described, adequate and reliable. Study conducted at reputable lab with study director with extensive experience.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Deviations:
- not applicable
- Principles of method if other than guideline:
- Because the majority (55%) of orally administered DPPD (N,N'-diphenyl-p-phenylenediamine) is exreted in feces of rats with <0.1% excreted in urine, this study was designed to focus on fecal excretion with a thorough assessment of biliary elimination of the test chemical N,N'-di-o-tolyl-p-phenylenediamine (R-898). This chemical is typically ~20% of the registration substance DAPD.
The R-898 molecule was synthesized with radioactivity (14C) positioned in the center ring. This radiotracer was added to the submission substance to allow quantitation of excreted material. The specific activity of the radiochemical was 11.66 mCi/mmol with 98.7% radiochemical purity.
One oral gavage dose administered to each rat. Three sampling sites were included in the study - urine, feces, and bile. Urine & fecal samples were collected at 6, 12, 24, 36, 48 & 72 hrs following dosing in the Phase 1 (intact) group. Sampling was terminated at 48 hrs in the Phase 2 group.
Samples were analyzed for radioactivity using liquid scintillation counting and HPLC with both UV and flow-thru scintillation counting. - GLP compliance:
- not specified
Test material
- Reference substance name:
- N-(2-methylphenyl)-N'-phenylbenzene-1,4-diamine
- Cas Number:
- 27173-16-6
- Molecular formula:
- C19 H18 N2
- IUPAC Name:
- N-(2-methylphenyl)-N'-phenylbenzene-1,4-diamine
- Reference substance name:
- N,N'-bis(2-methylphenyl)benzene-1,4-diamine
- EC Number:
- 239-102-7
- EC Name:
- N,N'-bis(2-methylphenyl)benzene-1,4-diamine
- Cas Number:
- 15017-02-4
- Molecular formula:
- C20H20N2
- IUPAC Name:
- N,N'-bis(2-methylphenyl)benzene-1,4-diamine
- Reference substance name:
- R-898 or N,N'-di-o-tolyl-p-phenylenediamine
- IUPAC Name:
- R-898 or N,N'-di-o-tolyl-p-phenylenediamine
- Details on test material:
- The test material was R-898 (N,N-di-o-tolyl-p-phenylenediamine), a major component of the submission substance DAPD. The molecular formula is C20H20N2 with molecular weight of 288.4. SMILES notation: Cc1ccccc1Nc2ccc(Nc3c(C)cccc3)cc2. The lot # was 960718A.
Test solutions were prepared by dissolving DAPD + [14C]R-898 in corn oil prior to oral gavage dosing. Two trials were performed - the dosing soln for the first trial (intact bile ducts) delivered a dose of 8.4 mg R-898/kg, 30.3 mg DAPD/kg, and ~21 uCi per rat. Prior to addition of [14C]R-898 to theDAPD in the dosing corn oil dosing solution, the submission substance was estimated to contain 23% of this component; after addition of [14C] material, 28%. Levels of R-898 in the submission substance was estimated using HPLC/UV quantitation.
The 2nd trial (bile ducts cannulated) delivered a dose of 7.4 mg R-898/kg, 26.7 mg DAPD/kg, and ~15 uCi per rat.
The lot numbers were 137170393 for the DAPD, and 91004140 for the labeled R-898.
Due to the very long shelf life of the submission substance (5 yr+), the stability of the radiolabel and chemicals in the dosing solution were considered to be assured under these conditions.
Constituent 1
Constituent 2
Constituent 3
- Radiolabelling:
- yes
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- Male rats were obtained from Charles River Labs, North Carolina. They were provided drinking water & Purina Rat chow ad libitum. Rats were housed 4 per cage during minimum of one-week acclimation period and until study initation. The environment was 73 +/- F degrees, 40-70% relative humidity, and with 12/12 hr photocycle. Each rat in group 2 (6 rats) was subjected to cannulations of the bile duct to provide delivery of bile. Following duct cannulations, the rats were allowed to recover for 48 hr before oral gavage dosing. Group 1 rats (4 rats) remained intact without cannulations.
At dosing, rats were individually housed in glass metabolism cages that provided separation of urine & feces. Body weights of rats were in the range of 216 to 251 grams at dosing. Rats were not fasted prior to dosing.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- The test solution was dosed in volume of 5 ml/kg. The submission substance was at a level of ~4 mg/ml in the dosing solution. Corn oil was used as it is common vehicle for animal oral gavage testing, and was shown to solubilize the test compound.
- Duration and frequency of treatment / exposure:
- One oral gavage dose administered to each rat.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Dose for Phase 1 was ~30 mg DAPD/kg plus ~8 mg R-898/kg, and for Phase 2, 27 mg DAPD/kg, 7 mg R-898/kg. The radioactivity doses were ~21 uCi rat in Phase 1, and ~15 uCi/rat in Phase 2.
- No. of animals per sex per dose / concentration:
- Males only were used in study. A total of 6 rats were cannulated for use in Phase 2. Due to poor health, only 4 rats were retained for collection of bile samples.
- Control animals:
- no
- Positive control reference chemical:
- No
- Details on study design:
- The dose employed was below that known to be toxic, but provided sufficient amount of chemical to allow measurements of excreted material following oral dosing. Animals were assigned in random manner.
- Details on dosing and sampling:
- Three sampling sites were included in the study - urine, feces, and bile. Urine & fecal samples were collected at 6, 12, 24, 36, 48 & 72 hrs following dosing in the Phase 1 (intact) group. Sampling was terminated at 48 hrs in the Phase 2 group.
Samples were analyzed for radioactivity using liquid scintillation counting and HPLC with both UV and flow-thru scintillation counting. - Statistics:
- Standard deviations were calculated for radioactivities collected.
Results and discussion
- Preliminary studies:
- None
Metabolite characterisation studies
- Metabolites identified:
- not measured
- Details on metabolites:
- Identification of metabolites was not conducted. However, HPLC profiles demonstrate (a) the parent compound R-898 in the bile is a minor fraction (<2.5%) of that collected in the bile, and (b) >90% of the bile radiolabel elutes in the HPL chromatographic region associated with metabolites exhibiting higher polarity than the parent cmpd. 40% of that radioactivity was located in one peak (B4).
Any other information on results incl. tables
Radioactivity Excreted Following Oral Dosing of [14C] R-898 to Intact Rats |
||||
14C [% of dose admin.] (S. Dev.) | ||||
Urine | Fecal | Total | ||
Ave. Amnts (n=4) | 1.1 (0.3) | 74.5 (6.1) | 75.5 (6.2) |
Radioactivity Excreted Following Oral Dosing of [14C] R-898 to Cannulated Rats |
|||||
14C [% of dose admin.] (S. Dev.) | |||||
Bile collected (g) | Bile | Urine | Fecal | Total | |
Ave. Amnts (n=4) | 30.2 (3.6) | 30.1 (7.3) | 0.6 (0.2) | 43.8 (4.3) | 74.4 (3.5) |
Bile Metabolites of [14C] R-898 Following Oral Administration to Cannulated Rats (% of Eluted 14C) |
|||
HPLC Peak | Retention Time (min) | Mean | SD |
B1 | 7.2 - 8.5 | 9.7 | 5.4 |
B2 | 8.5 - 10.7 | 16.8 | 6.2 |
B3 | 11.9 - 14.0 | 50.0 | 10.7 |
B4 (R-898) | 18.6 - 20.3 | 1.5 | 0.3 |
TOTAL | 78.0 |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): bioaccumulation potential cannot be judged based on study results
Oral administration of radioactive R-898, a major component of the submission substance, has shown the radioactivity is excreted primarily in the feces (75%). The biliary excretion accounted for ~40% of that amount. Urinary excretion was minor (<2.5%). Biliary metabolites were shown to be polar substances, accounting for >95% of the radioactivity excreted by this route. - Executive summary:
The study was designed to assess routes of excretion in rats of R-898, a major component of the submission substance. Urinary & fecal samples were collected over period up to 72 hrs following oral dosing in intact rats, up to 48 hrs in bile duct-cannulated animals. Results showed that ~75% of dosed radioactivity is excreted in feces with 30% of the dosed amount entering the GI tract via the biliary route. <2% was excreted in the urine. HPLC analysis of bile demonstrated that 95+ % of the metabolites excreted by this route exhibited greater polarity than the parent compound, suggesting metabolic formation of oxidation and conjugation products of this component.
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.