Registration Dossier
Registration Dossier
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: 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

Genetic toxicity: in vitro
Administrative data
- Endpoint:
- in vitro gene mutation study in bacteria
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Basic data given, acceptable for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- Salmonella Mutagenicity Tests: IV. Results From the Testing of 300 Chemicals
- Author:
- Zeiger E, et al.
- Year:
- 1 988
- Bibliographic source:
- Environ. Mol. Mutagen. 11, Suppl. 12, 1-158 (1988)
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- yes
- Remarks:
- only four strains tested; no strain included to identify cross-linking mutagens
- Principles of method if other than guideline:
- Standard plate incorporation according to Ames et al. (1975). Results of 300 tested chemicals were listed in tabular form.
- GLP compliance:
- not specified
- Type of assay:
- bacterial reverse mutation assay
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
- Details on test material:
- - Name of test material (as cited in study report): 2,6-Xylidine
- Supplier: Ethyl Corporation,
- Analytical purity: 99.1 % (Analyzed by Midwest Research Institute, Kansas City, MO .)
- no further data.
Constituent 1
Method
Species / strain
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Metabolic activation:
- with and without
- Metabolic activation system:
- rat and hamster liver S9 mix (Aroclor-induced)
- Test concentrations with justification for top dose:
- 10-3333 µg/plate
Controls
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: see details on test system and conditions
- Details on test system and experimental conditions:
- Tester strains
Salmonella typhimurium strains TA97, TA98, TA100, TA1535, and TA1537 were obtained from Dr. Bruce Ames (University of California, Berkeley) and were stored as recommended [Maron and Ames, 19831 . Cultures were grown overnight with shaking at 37° C in Oxoid No.2 broth, and their phenotypes were analyzed prior to their use for mutagenicity assays.
Preparation of Liver S-9 Fractions
The S9 (9,000g supernatant) fractions of Aroclor 1254-induced, male Sprague-Dawley rat and male Syrian hamster livers were prepared as described previously [Haworth et al, 1983]. The S9 mixes were prepared immediately prior to use and contained either 10 % or 30 % S9; occasionally, other levels were used. All chemicals were tested in the absence of
metabolic activation and with rat and hamster S-9 fractions.
Test Protocol
The preincubation assay was performed as described previously [Haworth et. al., 1983], with some differences, as described below. The test chemical (0.05 ml), Salmonella culture (0.1 ml), and S-9 mix or buffer (0.5 ml) were incubated at 37°C, without shaking, for 20 min. Chemicals known or suspected to be volatile were incubated in capped tubes. The top agar was added and the contents of the tubes were mixed and poured onto the surface of petri dishes containing Vogel-Bonner medium [Vogel and Bonner, 1956]. The histidine-independent (his+) colonies arising on these plates were counted following two days incubation at 37°C. Plates were
machine counted (New Brunswick, Edison, NJ; Artek, Farmingdale, NY) unless precipitate was present which interfered with the count, or the color of the test chemical on the plate reduced the contrast between the colonies and the background agar. At the discretion of the investigators, plates with low numbers of colonies were counted by hand. Variations in the protocol among the tested chemicals reflect the evolution of the protocol originally described by Haworth et al. [1983] . Four protocol variations are evident from the data in Appendix 2 .
1) Testing in strains TA97, TA98, TA100, and TA1535, with some additional testing in strain TA1537 ; 10% S-9 was used.
2) The first test of a chemical was without activation and with 10 % S-9 in the S-9 mix. If a positive result was obtained the test was repeated. If the tests were negative they were repeated without S-9 and with 30 % S-9.
3) The order of use of 10% and 30% S9 was reversed.
4) Initial testing was in strains TA98 and TA 100 without activation and with 30 % rat and hamster S9s. If a positive result was obtained in one of these two strains it was repeated and the other strains were not used. If the tests were negative, the other strains were used with 30 % and10 % S9. A chemical was not designated non-mutagenic unless it had been tested in strains TA98, TA100, TA1535, and TA97 and/or TA 1537, without activation and with 10 % and 30 % rat and hamster S9. Occasionally, 5 % S9 was also used in all protocol variations. All chemicals were tested initially in a toxicity assay to determine the appropriate dose range for the mutagenicity assay . The toxicity assay was performed using TA 100 or the system developed by Waleh et al . [1982]. Toxic concentrations were those that produced a decrease in the number of his+ colonies, or a clearing in the density of the background lawn, or both. Each chemical was tested initially at half-log dose intervals up to a dose that elicited toxicity, or to a dose immediately below one which was toxic in the preliminary toxicity test. Subsequent trials occasionally used narrower dose increments and may not have included doses in the toxic range. Chemicals that were not toxic were tested, with few exceptions, to a maximum dose of 10 mg/plate. Chemicals that were poorly soluble were tested up to doses defined by their solubilities. At least five doses of each chemical were tested in triplicate. Experiments were repeated at least one week following the initial trial. A maximum of 0.05 ml solvent was added to each plate. Concurrent solvent and positive controls were run with each trial. The positive controls in the absence of metabolic activation were sodium azide (TA1535 and TA100), 9-aminoacridine (TA97 and TA1537), and 4-nitro-o-henylenediamine
(TA98). The positive control for metabolic activation with all strains was 2-aminoanthracene.
Occasionally, a laboratory used a single solvent and/or positive control for more than one chemical tested on the same day. Each laboratory made its own determination regarding positive control dose levels. - Evaluation criteria:
- The data were evaluated as described previously [Zeiger et al. 1987]. Evaluations were made at both the individual trial and overall chemical levels. Individual trials were judged mutagenic (+), weakly mutagenic (+W), questionable (?), or non-mutagenic (-), depending on the magnitude of the increase of his+ revertants, and the shape of the dose-response. A trial was considered questionable (?) if the dose-response was judged insufficiently high to support a call of "+W," if only a single dose was elevated over the control, or if the increase seen was not dose related. The distinctions between a questionable mutagenic response and a non-mutagenic or weak mutagenic response, and between a weak mutagenic response and mutagenic response are highly subjective. It was not necessary for a response to reach twofold over background for a chemical to be judged mutagenic. A chemical was judged mutagenic (+) or weakly mutagenic (+W) if it produced a reproducible dose-related response over the solvent control in replicate trials. A chemical was judged questionable (?) if the results of individual trials were not reproducible, if increases in his+ revertants did not meet the criteria for a "+W" response, or if only single doses produced increases in his+ revertants in repeat trials. Chemicals were judged non-mutagenic (-) if they did not meet the criteria for a mutagenic or questionable response. The chemicals were decoded by the chemical repository only after a determination had been made regarding their mutagenicity or non-mutagenicity.
Results and discussion
Test results
- Species / strain:
- other: Salmonella typhimurium; TA 97, 98, 100, 1535, 1537
- Metabolic activation:
- with and without
- Genotoxicity:
- ambiguous
- Cytotoxicity / choice of top concentrations:
- not specified
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Remarks on result:
- other: other: Salmonella typhimurium; TA 97, 98, 100, 1535, 1537
- Remarks:
- Migrated from field 'Test system'.
Any other information on results incl. tables
2,6-xylidine produced only weak positve results with the tester strains investigated. Results of 3 independent laboratories judged the test substance as weakly positive ( Microbiological Associates, Inc . (MIC) and SRI International (SRI)) or negative (Case Western Reserve University (CWR) ).
Applicant's summary and conclusion
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.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.