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EC number: 249-204-3 | CAS number: 28768-32-3
- 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:
- 18 October 2012 and 30 October 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of the relevant results.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 012
- Report date:
- 2012
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- 2012-07-10
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- 4,4'-methylenebis[N,N-bis(2,3-epoxypropyl)aniline]:
- IUPAC Name:
- 4,4'-methylenebis[N,N-bis(2,3-epoxypropyl)aniline]:
- Test material form:
- liquid: viscous
- Details on test material:
- Sponsor's identification: 4,4'-methylenebis[N,N-bis(2,3-epoxypropyl)aniline]
Description: amber coloured extremely viscous liquid
Batch number: AAB0290400
Purity: 100%
Date received: 21 August 2012
Expiry date : 01 February 2014
Storage conditions: approximately 4°C in the dark
Constituent 1
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- other: CBA/Ca (CBA/CaOlaHsd)
- Sex:
- female
- Details on test animals and environmental conditions:
- Female CBA/Ca (CBA/CaOlaHsd) strain mice were supplied by Harlan Laboratories UK Ltd., Oxon, UK. On receipt the animals were randomly allocated to cages. The animals were nulliparous and non pregnant. After an acclimatisation period of at least five days the animals were selected at random and given a number unique within the study by indelible ink marking on the tail and a number written on a cage card. At the start of the study the animals were in the weight range of 15 to 23 g, and were eight to twelve weeks old.
The animals were individually housed in suspended solid floor polypropylene cages furnished with softwood woodflakes. Free access to mains tap water and food (2014C Teklad Global Rodent diet supplied by Harlan Laboratories UK Ltd., Oxon, UK) was allowed throughout the study.
The temperature and relative humidity were controlled to remain within target ranges of 19 to 25°C and 30 to 70%, respectively. Any occasional deviations from these targets were considered not to have affected the purpose or integrity of the study. The rate of air exchange was approximately fifteen changes per hour and the lighting was controlled by a time switch to give twelve hours continuous light (06.00 to 18.00) and twelve hours darkness.
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.
Study design: in vivo (LLNA)
- Vehicle:
- dimethylformamide
- Concentration:
- Preliminary Screening Test : 50% w/w in dimethyl formamide
Main test: 50%, 25% or 10% w/w in dimethyl formamide - No. of animals per dose:
- 4
- Details on study design:
- Preliminary Screening Test
As no toxicological information was available regarding the systemic toxicity/irritancy potential of the test item, a preliminary screening test was performed using one mouse. The mouse was treated by daily application of 25 µl at a concentration of 50% w/w in dimethyl formamide, to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3). The mouse was observed twice daily on Days 1, 2 and 3 and once daily on Days 4, 5 and 6. Local skin irritation was scored daily according to the scale included as Appendix 4. Any clinical signs of toxicity, if present, were also recorded. The bodyweight was recorded on Day 1 (prior to dosing) and on Day 6
The thickness of each ear was measured using an Oditest micrometer (Dyer, PA), pre dose on Day 1, post dose on Day 3 and on Day 6. Any changes in the ear thickness were noted. Mean ear thickness changes were calculated between time periods Days 1 and 3 and Days 1 and 6. A mean ear thickness increase of equal to or greater than 25% was considered to indicate excessive irritation and limited biological relevance to the endpoint of sensitisation.
Main Test
Test Item Administration
Groups of four mice were treated with the test item at concentrations of 50%, 25% or 10% w/w in dimethyl formamide. The preliminary screening test suggested that the test item would not produce systemic toxicity or excessive local skin irritation at the highest suitable concentration. The mice were treated by daily application of 25 µl of the appropriate concentration of the test item to the dorsal surface of each ear for three consecutive days (Days 1, 2, 3). The test item 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 in the same manner.
3H-Methyl Thymidine Administration
Five days following the first topical application of the test item or vehicle (Day 6) all mice were injected via the tail vein with 250 µl of phosphate buffered saline (PBS) containing 3H methyl thymidine (3HTdR: 80 µCi/ml, specific activity 2.0 Ci/mmol, ARC UK Ltd) giving a total of 20 µCi to each mouse.
Observations
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 test were recorded.
Bodyweights: The bodyweight of each mouse was recorded on Day 1 (prior to dosing) and Day 6 (prior to termination).
Terminal Procedures
Termination: Five hours following the 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 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 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 precipitate out the radioactive material, the pellet was resuspended in 3 ml of 5% Trichloroacetic acid (TCA).
Determination of 3HTdR Incorporation: After approximately eighteen hours incubation at approximately 4°C, 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 scintillation counting. The "Poly QTM" vials containing the samples and scintillation fluid were placed in the sample changer of the scintillator and left for approximately twenty minutes. The purpose of this period of time in darkness was to reduce the risk of luminescence, which has been shown to affect the reliability of the results. After approximately twenty minutes, the vials were shaken vigorously. The number of radioactive disintegrations per minute was then measured using the Beckman LS6500 scintillation system (Beckman Instruments Inc, Fullerton, CA, USA). - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- No statistics used in this test.
Results and discussion
In vivo (LLNA)
Resultsopen allclose all
- Key result
- Parameter:
- SI
- Value:
- > 5.97 - < 11.18
- Test group / Remarks:
- See # of animals per group
- Remarks on result:
- other: The group stimulation indices are given in Table 4.
- Key result
- Parameter:
- SI
- Value:
- > 5.79 - < 11.18
- Test group / Remarks:
- See # of animals per group
- Remarks on result:
- other: The radioactive disintegrations per minute per lymph node and the stimulation index are given in Table 4.
Any other information on results incl. tables
Clinical Observations and Mortality Data
Individual clinical observations and mortality data for test and control animals are given in Table 5.
There were no deaths. No signs of systemic toxicity were noted in the test or control animals during the test
Bodyweight
Individual bodyweights and bodyweight changes for test and control animals are given in Table 6.
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.
Table 4 Disintegrations per Minute, Disintegrations per Minute/Node and Stimulation Index
Concentration |
dpm |
dpm/Nodea |
Stimulation Indexb |
Result |
Vehicle |
16555.72 |
2069.47 |
na |
na |
10 |
98774.97 |
12346.87 |
5.97 |
positive |
25 |
98880.57 |
12360.07 |
5.97 |
positive |
50 |
184966.80 |
23120.85 |
11.17 |
positive |
dpm= Disintegrations per minute
a= Disintegrations per minute/node obtained by dividing the disintegrations per minute value by 8 (total number of lymph nodes)
b= Stimulation Index of 3.0 or greater indicates a positive result
na = Not applicable
Table 5 Individual Clinical Observations and Mortality Data
Concentration |
Animal Number |
Day 1 |
Day 2 |
Day 3 |
Day 4 |
Day 5 |
Day 6 |
||||||||||||||
Pre-Dose |
Post Dose |
Pre-Dose |
Post Dose |
Pre-Dose |
Post Dose |
||||||||||||||||
Vehicle |
1-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||||||||||
1-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||||||||||||
1-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||||||||||||
1-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||||||||||||
10 |
2-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||||||||||
2-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||||||||||||
2-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||||||||||||
2-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||||||||||||
25 |
3-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||||||||||
3-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||||||||||||
3-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||||||||||||
3-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||||||||||||
50 |
4-1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
|||||||||||
4-2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||||||||||||
4-3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
||||||||||||
4-4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0= No signs of systemic toxicity
Table 6 Individual Bodyweights and Bodyweight Changes
Concentration |
Animal Number |
Bodyweight (g) |
Bodyweight Change (g) |
|
Day 1 |
Day 6 |
|||
Vehicle |
1-1 |
20 |
23 |
3 |
1-2 |
22 |
24 |
2 |
|
1-3 |
20 |
21 |
1 |
|
1-4 |
22 |
23 |
1 |
|
10 |
2-1 |
20 |
22 |
2 |
2-2 |
20 |
21 |
1 |
|
2-3 |
21 |
23 |
2 |
|
2-4 |
20 |
22 |
2 |
|
25 |
3-1 |
19 |
20 |
1 |
3-2 |
20 |
20 |
0 |
|
3-3 |
19 |
20 |
1 |
|
3-4 |
20 |
21 |
1 |
|
50 |
4-1 |
21 |
21 |
0 |
4-2 |
21 |
20 |
-1 |
|
4-3 |
17 |
17 |
0 |
|
4-4 |
18 |
19 |
1 |
dpm= Disintegrations per minute
a= Disintegrations per minute/node obtained by dividing the disintegrations per minute value by 8 (total number of lymph nodes)
b= Stimulation Index of 3.0 or greater indicates a positive result
Applicant's summary and conclusion
- Interpretation of results:
- sensitising
- Remarks:
- Migrated information Criteria used for interpretation of results: expert judgment
- Conclusions:
- The test item was considered to be a sensitiser under the conditions of the test.
- Executive summary:
Introduction.
A study was performed to assess the skin sensitisation potential of the test item in the CBA/Ca strain mouse following topical application to the dorsal surface of the ear. The method was designed tobe compatible withthe following:
§ OECD Guideline for the Testing of Chemicals No. 429 "Skin Sensitisation: Local Lymph Node Assay" (adopted 22 July 2010)
§ Method B42 Skin Sensitisation (Local Lymph Node Assay) of CommissionRegulation (EC) No. 440/2008
Methods.
Following a preliminary screening test in which no clinical signs of toxicity were noted at a concentration of 50% w/w, this concentration was selected as the highest dose investigated in the main test of the Local Lymph Node Assay. Three groups, each of four animals, were treated with 50 µl (25 µl per ear) the test item as a solution in dimethyl formamide at concentrations of 50%, 25% or 10% w/w. A further group of four animals was treated with dimethyl formamide alone.
Results.
The Stimulation Index expressed as the mean radioactive incorporation for each treatment group divided by the mean radioactive incorporation of the vehicle control group are as follows:
Concentration (%w/w) in
dimethyl formamideStimulation Index
Result
10
5.97
positive
25
5.97
positive
50
11.17
positive
Conclusion.
The test item was considered to be a sensitiser under the conditions of the test.
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