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EC number: 216-032-5 | CAS number: 1477-55-0
- 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
Skin sensitisation
Administrative data
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2004-03-03 to 2004-06-04
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 004
- Report date:
- 2004
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Date of inspection 2002-12-04; Date of signature 2003-02-13
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- m-phenylenebis(methylamine)
- EC Number:
- 216-032-5
- EC Name:
- m-phenylenebis(methylamine)
- Cas Number:
- 1477-55-0
- Molecular formula:
- C8H12N2
- IUPAC Name:
- 1-[3-(aminomethyl)phenyl]methanamine
- Test material form:
- liquid
- Details on test material:
- - Name of test material (as cited in study report): MXDA
- Physical state: Colourless liquid
- Storage condition of test material: Room temperature in the dark
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- other: CBA/Ca (CBA/CaBkl)
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: B & K Universal Ltd, Hull, UK
- Age at study initiation: 8-12 weeks
- Weight at study initiation: 15-23 g
- Housing: Individually in suspended solid-floor polypropylene cages furnished with softwood woodflakes. The animals were provided with environmental enrichment items which were considered not to contain any contaminant of a level that might have affected the purpose or integrity of the study.
- Diet: Free access to Certified Rat and Mouse Diet (Code 5LF2) supplied by BCM IPS Limited, London, UK
- Water: Free access to mains tap water
- Acclimation period: At least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 19-25 degrees Centigrade
- Humidity: 30-70 %
- Air changes: Approximately 15 per hour
- Photoperiod: Controlled by a time switch to give twelve hours continuous light (06:00 to 18:00) and twelve hours darkness
Study design: in vivo (LLNA)
- Vehicle:
- dimethylformamide
- Concentration:
- Preliminary screening test: Undiluted test material, or test material at a concentration of 10 % or 25 % in dimethyl formamide
Main test: zero %, 2.5 %, 5 % or 10 % test material in dimethyl formamide - No. of animals per dose:
- Preliminary screening test: Three
Main test: Four per dose level - Details on study design:
- PRELIMINARY SCREENING TEST
As no toxicological information was available regarding the systemic toxicity/irritancy potential of the test material, a preliminary screening test was performed using three mice. The mice were treated by daily application of 25 μL of the undiluted test material, or test material dilutions of 25 % or 10 % in dimethyl formamide, to the dorsal surface of each ear for three consecutive days (Days 1, 2 and 3). The mice were observed twice daily on Days 1, 2 and 3 and once daily on Days 4, 5, and 6. The mice treated with the undiluted test material and the test material at a concentration of 25 % were killed for humane reasons due to signs of systemic toxicity. Observations for these animals were performed accordingly. Any signs of toxicity or excessive local irritation noted during this period were recorded. The bodyweight of each mouse was recorded on Day 1 (prior to dosing) and of the surviving mouse on Day 6.
MAIN TEST
Groups of four mice were treated with the test material at concentrations of 2.5 %, 5 % or 10 % v/v in dimethyl formamide. The preliminary screening test suggested that the test material would not produce systemic toxicity or excessive local irritation at the highest suitable concentration. The mice were treated by daily application of 25 μL of the appropriate concentration to the dorsal surface of each ear for three consecutive days (Days 1, 2 and 3). The test material formulation was administered using an automatic micropipette and spread over the dorsal surface of the ear using the tip of the pipette. A further group of four mice received the vehicle alone via the same application method.
3H-METHYL THYMIDINE ADMINISTRATION
Five days following the first topical application of the test material (Day 6) all mice were injected via the tail vein with 250 μL of phosphate buffered saline containing 3H-methyl thymidine (3HTdR:80 μCi/mL, specific activity 2.0 Ci/mmoL, Amershal Biosciences UK Ltd) giving a total of 20 μCi to each mouse.
CLINICAL OBSERVATIONS
All animals were observed twice daily on Days 1, 2 and 3 and on a daily basis on Days 4, 5 and 6. Any signs of toxicity or signs of ill health during the study were recorded.
BODYWEIGHTS
The bodyweight of each mouse was recorded on Day 1 (prior to dosing) and Day 6 (prior to termination)
TERMINATION
Five hours after administration of 3HTdR, all mice were killed by carbon dioxide asphyxiation. The draining auricular lymph nodes from the four mice were excised and pooled for each experimental group. For each group, 1 mL of phosphate buffered saline (PBS) was added to the pooled lymph nodes.
PREPARATION OF SINGLE CELL SUSPENSION
A single cell suspension of pooled lymph node cells was prepared by gentle mechanical disaggregation through a 200-mesh stainless steel gauze. The lymph node cells were rinsed through the gauze with 4 mL of PBS into a petri dish labelled with the project number and dose concentration. The lymph node cell suspension was transferred to a 10 mL centrifuge tube. The petri dish was washed with an additional 5 mL of PBS to remove all remaining lymph node cells and these were added to the centrifuge tube. The pooled lymph node cells were pelleted at 1400 rpm (approximately 190 g) for ten minutes. The pellet was resuspended in 10 mL of PBS and re-pelleted. To preceipitate out the radioactive material, the pellet was resuspended in 3 mL of 5 % trichloroacetic acid (TCA).
DETERMINATION OF 3HTdR INCORPORATION
After overnight incubation at 4 degrees Centigrade, the precipitates were recovered by centrifugation at 2100 rpm (approximately 450 g) for ten minutes, resuspended in 1 mL of TCA and transferred to 10 mL of scintillation fluid (Optiphase Trisafe). 3HTdR incorporation was measured by β-scintillation counting. The Poly Q vials containing the samples and scintillation fluid were placed in the sample chamber of the scintillator and left for approximately twenty minutes. The period of time in darkness was used to reduce the risk of luminescence, which has been shown to affect reliabilty of results. After approximately 20 minutes, the vials were shaken vigorously and the number of radioactive disintegrations per minute measured using the Beckman LS6500 scintillation system (Beckman Instruments Inc, Fullerton, CA).
INTERPRETATION OF RESULTS
The test substance was regarded as a sensitiser if at least one concentration resulted in a threefold or greater increase in 3HTdR incorporation compared to control values. Any test material failing to produce a threefold or greater increase in 3HTdR incorporation was classified as a non-sensitiser. - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- The proliferation response of lymph node cells was expressed as the number of radioactive disintegrations per minute per lymph node (dpm/node) and as a ratio of 3HTdR incorporation into lymph node cells of test nodes relative to that recorded for the control nodes (Stimulation Index).
Results and discussion
- Positive control results:
- See Appendix 1 (attached)
In vivo (LLNA)
Resultsopen allclose all
- Key result
- Parameter:
- SI
- Value:
- 1.63
- Test group / Remarks:
- 2.5%
- Key result
- Parameter:
- SI
- Value:
- 5.21
- Test group / Remarks:
- 5%
- Key result
- Parameter:
- SI
- Value:
- 3.66
- Test group / Remarks:
- 10%
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: See Table 2 (attached)
Any other information on results incl. tables
PRELIMINARY SCREENING TEST
Clinical observations, bodyweight and mortality data are given in Table 1 (attached). The animals treated with undiluted test material at a concentration of 25 % v/v in dimethyl formamide were killed for humane reasons on days 1 and 2 respectively due to signs of systemic toxicity including hunched posture and ptosis. There were no signs of systemic toxicity noted in the mouse treated at a concentration of 10 % v/v in dimethyl formamide. Based on this information, the dose levels selected for the main test were 2.5 %, 5 % and 10 % v/v in dimethyl formamide.
MAIN TEST
CLINICAL OBSERVATIONS AND MORTALITY DATA
Individual clinical observations and mortality data for test and control animals are given in Table 3 (attached). There were no deaths. No signs of systemic toxicity were noted in the test or control animals during the study. White residual test material was noted on the fur and ears of animals treated with the test material at concentrations of 5 % and 10 % v/v in dimethyl formamide.
BODYWEIGHT
Individual bodyweights and bodyweight changes for test and control animals are given in Table 4 (attached). Bodyweight changes of the test animals between Day 1 and Day 6 were comparable to those observed in the corresponding control group animals over the same period.
Applicant's summary and conclusion
- Interpretation of results:
- sensitising
- Remarks:
- Migrated information
- Conclusions:
- The test material was considered to be a sensitiser under the conditions of the test.
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