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EC number: 201-758-7 | CAS number: 87-62-7
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- 24 April 2002
- Deviations:
- yes
- Remarks:
- relative humidity: 25 - 67% (guideline 30-70%)
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Version / remarks:
- 30 May 2008
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.2600 (Skin Sensitisation)
- Version / remarks:
- March 2003
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Hess. Ministerium für Umwelt, Energie, Landwirtschaft und Verbraucherschutz, Mainzer Straße 80, D-65189 Wiesbaden
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- 2,6-xylidine
- EC Number:
- 201-758-7
- EC Name:
- 2,6-xylidine
- Cas Number:
- 87-62-7
- Molecular formula:
- C8H11N
- IUPAC Name:
- 2,6-dimethylaniline
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- - Analytical purity: concomitantly analysed; dose calculation not adjusted to purity
- Lot/batch No.: 000STD77L0
- Expiration date of the lot/batch: December 15, 2011
- Stability under test conditions: verified indirectly by concentration control analysis
- Storage condition of test material: room temperature
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Harlan Laboratories B.V., Postbus 6174, 5960 AD Horst / The Netherlands
- Age at study initiation: 8 - 12 weeks
- Weight at study initiation:
- Housing: single in Makrolon Type II, with wire mesh top (EHRET GmbH, 79302 Emmendingen, Germany)
- Diet (e.g. ad libitum): pelleted standard diet, ad libitum (Harlan Laboratories B.V. 5960 AD Horst / Netherlands)
- Water (e.g. ad libitum): tap water
- Acclimation period: at least 5 days prior to the start of dosing under test conditions after health examination. Only animals without any visible signs of illness were used for the study
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22±2
- Humidity (%): 25 - 67
- Air changes (per hr):
- Photoperiod (hrs dark / hrs light): 12 / 12
Study design: in vivo (LLNA)
- Vehicle:
- methyl ethyl ketone
- Remarks:
- Methyl ethyl ketone (purity 99% from Sigma-Aldrich Chemie GmbH (89555 Steinheim, Germany)
- Concentration:
- 0, 5, 10 or 25% (w/v) in vehicle
- No. of animals per dose:
- 5 (2 for the 2 pre-test groups)
- Details on study design:
- RANGE FINDING TESTS:
- Compound solubility: the highest test item concentration, which could be technically used, was 100% of the undiluted test item. Upon sponsor’s request, the solutions were formulated in methyl ethyl ketone. Vortexing was necessary to formulate the test item
- Irritation: to previously confirm the appropriateness of the concentrations intended for use in the main experiment, a pre-test was performed using 50 and 100% test substance concentration. During the pre-test, both animals showed signs of systemic toxicity and the animal treated with 100% undiluted test substance was found dead within one hour after the second application. Thus, a second pre-test was performed using test substance concentrations of 10 and 25% (w/v). At these concentrations the animals did not show any signs of systemic toxicity or signs of local skin irritation. Therefore, in this study, three groups each of five female mice were treated with 5, 10 or 25% (w/v) test substance concentration by topical application at the dorsum of each ear on three consecutive days.
- Lymph node proliferation response: only ear thickness and ear weight measurements.
MAIN STUDY
ANIMAL ASSIGNMENT AND TREATMENT
- Name of test method: LLNA
- Criteria used to consider a positive response: a test item is regarded as a sensitiser in the LLNA if the following criteria are fulfilled: (1) exposure to at least one concentration of the test item resulted in an incorporation of 3HTdR at least 3-fold or greater than that recorded in control mice, as indicated by the stimulation index; and (2) the data are compatible with a conventional dose response, although allowance must be made (especially at high topical concentrations) for either local toxicity or immunological suppression.
The estimated concentration of test item required to produce a S.I. of 3 is referred to as the EC3 value.
TREATMENT PREPARATION AND ADMINISTRATION:
- each test group of mice was treated by topical (epidermal) application to the dorsal surface of each ear (left and right; entire dorsal surface of 8 mm diameter) of 25 µl test item concentrations in vehicle (methyl ethyl ketone ) or its vehicle alone or with the positive control item at 25% (w/v in acetone:olive oil 4:1), or acetone:olive oil 4:1 alone, once daily for three consecutive days.
- Five days after the first topical application, 250 µl of 79.7 µCi/ml of 3H-methyl thymidine (3HTdR; purchased from Hartmann Analytic, 38124 Braunschweig, Germany; specific activity, 2 Ci/mmol; concentration, 1 mCi/ml) were administered (i.v.) to the test animals via the tail vein.
- Approximately five hours after treatment with 3HTdR all mice were euthanized by intraperitoneal injection of Pentobarbital-Natrium. The draining lymph nodes were rapidly excised and pooled per animal (2 nodes per animal), and single cell suspensions (in phosphate buffered saline) of pooled lymph node cells were prepared by gentle mechanical disaggregation through stainless steel gauze. After washing two times, the lymph node cells were resuspended in 5 % trichloroacetic acid (approx. 3 ml) and incubated at approximately +4 °C for at least 18 hours for precipitation of macromolecules. The precipitates were then resuspended in 5 % trichloroacetic acid (1 ml) and transferred to plastic scintillation vials with 10 ml of ‘Ultima Gold’ scintillation liquid and thoroughly mixed.
The level of 3HTdR incorporation was then measured on a β-scintillation counter (Tricarb 2900 TR, Perkin Elmer (LAS) GmbH, 63110 Rodgau, Germany). Similarly, background 3HTdR levels were also measured in two 1ml-aliquots of 5 % trichloroacetic acid. The β-scintillation counter expresses 3HTdR incorporation as the number of radioactive disintegrations per minute (DPM).
- After the lymph nodes had been excised, both ears (left and right) of mice were punched at the apical area using a biopsy punch (approx. 0.5 cm2). For each animal both punches were immediately weighed per animal using an analytical balance. - Positive control substance(s):
- hexyl cinnamic aldehyde (CAS No 101-86-0)
- Statistics:
- For all statistical calculations SigmaStat for Windows (Version 2.0) was used. A One-Way-Analysis-of-Variance was used as statistical method. In case of significant results of the One-Way-ANOVA, multiple comparisons were performed with the Dunnett test. However, the primary point of consideration was the biological relevance of the results.
A statistical analysis was conducted on the DPM/animal values and on the ear weights to assess whether the difference is statistically significant between test item groups and negative control (vehicle) group and also to assess if there is a dose response relationship.
Results and discussion
- Positive control results:
- The mean disintegrations per minute was, 858.2 in the test group 5 (control group for the positive control) and 6416.6 in the test group 6 (positive control group). The corresponding mean stimulation index for the test group 6 was 7.5 (see Table 2), thus clearly positive according to the criteria used to consider a positive response (SI > 3).
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Value:
- 2.21
- Test group / Remarks:
- 5%
- Parameter:
- SI
- Value:
- 1.78
- Test group / Remarks:
- 10%
- Parameter:
- SI
- Value:
- 2.75
- Test group / Remarks:
- 25%
- Parameter:
- EC3
- Remarks on result:
- other: The EC3 value could not be calculated, since all S.I.´s are below 3.
- Parameter:
- other: disintegrations per minute (DPM)
- Remarks on result:
- other: The mean disintegrations per minute was 493.0 in the test group 1(control group for the test item) 1089.6, 875.4 and 1356.6, respectively in the test groups 2, 3 and 4 (test item treated groups); see Table 2.
Any other information on results incl. tables
Table 2: Calculation of Stimulation Indices per Dose Group
Test item concentration |
Mean DPM per Group (5 animals)a) |
SDb) |
S.I. |
Vehicle for the Test Item (methyl ethyl ketone) |
492.5 |
110.3 |
1.00 |
5% 2,6-Xylidine |
1089.1S |
246.2 |
2.21 |
10% 2,6-Xylidine |
874.9 |
280.6 |
1.78 |
25% 2,6-Xylidine |
1356.1S |
486.2 |
2.75 |
Vehicle for the Positive Control (acetone:olive oil (4+1)) |
857.7 |
196.7 |
1.00 |
25% Positive Control |
6416.1S |
1837.4 |
7.48 |
a): mean DPM/Group was determined by dividing the sum of the measured values from lymph nodes of all animals within a group by the number of animals in that group (5 animals)b): SD= standard deviationS: statistically significant increase in comparison to the relevant control (vehicle) group (p<0.05)
|
ADDITIONAL RESULTS
- Viability / Mortality: no deaths occurred during the study period.
- Clinical Signs: no symptoms of local toxicity at the ears of the animals and no systemic findings were observed during the study period.
- Body Weights: the body weight of the animals, recorded prior to the first application and prior to treatment with 3HTdR, was within the range commonly recorded for animals of this strain and age.
- Ear Weights: the measured ear weights of all animals treated were recorded after sacrifice. A statistically significant increase in ear weights was not observed in any of the groups treated with different concentrations of the test item in comparison to the vehicle control group.
Applicant's summary and conclusion
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- The test item 2,6-Xylidine was not a skin sensitiser under the test conditions of this study.
- Executive summary:
In this study the test item 2,6-Xylidine dissolved in methyl ethyl ketone was assessed for its skin sensitizing potential using the Local Lymph Node Assay (LLNA) in mice.
The highest test item concentration, which could be technically used, was 100% of the undiluted test item. The solutions were formulated in methyl ethyl ketone. To previously confirm the appropriateness of the concentrations intended for use in the main experiment, a pre-experiment was performed using 50 and 100% test item concentration. During the pre-experiment, both animals showed signs of systemic toxicity and the animal treated with 100% undiluted test item was found dead within one hour after the second application. Thus, a second pre-test was performed using test item concentrations of 10 and 25% (w/v). At these concentrations the animals did not show any signs of systemic toxicity or signs of local skin irritation. Therefore, in this study, three groups each of five female mice were treated with 5, 10 or 25% (w/v) test item concentration by topical application at the dorsum of each ear on three consecutive days. The top dose was the highest test item concentration that could be used without inducing systemic toxicity or excessive local irritation. Two negative control groups were treated with the respective vehicle only (methyl ethyl ketone for the test item or acetone:olive oil (4+1) for the positive control item). A further group of five mice was treated with the positive control item. Five days after the first topical application, the mice were intravenously injected into a tail vein with radio-labelled thymidine (3H-methyl thymidine). Approximately five hours after intravenous injection, the mice were sacrificed, the draining auricular lymph nodes excised and pooled per animal. Additionally, the ears of the animals were punched at the apical area using a biopsy punch, pooled per animal and immediately weighed using an analytical balance. Single cell suspensions of lymph node cells pooled per animal were prepared and lymphocyte proliferation was quantified by measuring the incorporation of radiolabelled thymidine into the lymph node cells by beta-Scintillation Counting.
The animals did not show any signs of systemic toxicity during the course of the study and no cases of mortality were observed. Signs of local irritation (e.g. reddening of the ear skin, ear swelling) were also not observed during the study period. A statistically significant increase in ear weights was not observed in any of the groups treated with different concentrations of the test item in comparison to the vehicle control group. Here, Stimulation Indices (S.I.) of 2.21, 1.78 and 2.75 were determined with the test item at concentrations of 5, 10 and 25% (w/v) in methyl ethyl ketone, respectively. A statistically significant increase in DPM/animal values was observed in the groups treated with 5 and 25% test item concentration in comparison to the vehicle control group (p=0.003). However, this is not considered as biologically relevant as none of the S.I.s determined for these concentrations exceeded the threshold of 3 and as no clear dose response was observed for the tested concentrations. The EC3 value could not be calculated, since none of the tested concentrations induced an S.I. greater than 3. The S.I. of the positive control group was 7.48.
Conclusion: The test item 2,6-Xylidine did not show skin sensitizing potential in this assay under the conditions of this study.
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