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EC number: 219-283-9 | CAS number: 2402-79-1
- 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
- Study period:
- 9 July 1991 to 17 December 1991
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: GLP study conducted to a method equivalent to agreed protocols, but with the deviation that only four strains of bacteria were tested.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 991
- Report date:
- 1991
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- yes
- Remarks:
- Only 4 strains of Salmonella typhimurium were tested
- GLP compliance:
- yes
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- 2,3,5,6-tetrachloropyridine
- EC Number:
- 219-283-9
- EC Name:
- 2,3,5,6-tetrachloropyridine
- Cas Number:
- 2402-79-1
- Molecular formula:
- C5HCl4N
- IUPAC Name:
- 2,3,5,6-tetrachloropyridine
- Details on test material:
- Batch number WP-900914-748
Purity = 98.6%
Constituent 1
Method
- Target gene:
- Not applicable
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:
- Aroclor-induced rat liver S9
- Test concentrations with justification for top dose:
- 0.5 µg/plate to 50 µg/plate without metabolic activation
1.67 µg/plate to 166.7 µg/plate with metabolic activation - Vehicle / solvent:
- Dimethyl sulfoxide (DMSO)
- Details on test system and experimental conditions:
- Mutagenicity Assay
The pre-incubation modification of the standard Ames plate incorporation assay (Yahagi et al., 1975) was employed to optimize the contact between the bacteria and test chemical. The bacteria, test chemical, and if necessary, an activation mixture were incubated in sterile 12 x 75 mm tightly capped culture tubes in a gyratory incubator (300 RPM) at 30°C for 30 minutes. After the 30 minute incubation, 2 ml of supplemented top agar were added, the overlay poured onto plates, and the plates were placed in a 37°C incubator for approximately 2 days. All negative and positive controls were also pre-incubated. The total volume of incubation mixture was 0.7 ml and included:
(a) 0.5 ml of S-9 activation mixture (Table III) or 0.5 ml of 0.2 M sodium phosphate buffer, pH 7.4,
(b) 0.1 ml of an overnight bacterial culture, and
(c) 0.1 ml of test chemical solution or solvent.
Test Concentrations
The test material was dissolved in DMSO. Concentrations of the test material in the DMSO stock solution used for mutagenicity assays were verified by HPLC (Hinze, 1991). The negative control (solvent) plates consisted only of bacterial culture, 0.5 ml of 0.2 M sodium phosphate buffer or 0.5 ml S-9 activation mixture, and 0.1 ml of solvent. All positive controls were prepared in DMSO except for sodium azide, which was prepared in distilled water. All dose levels along with the positive and negative controls were assayed in triplicate in each experiment. Two independent experiments were conducted with each strain.
The test agent was initially assayed in TA100 at various dose levels. The concentrations tested in the subsequent assays were based upon the toxicity evaluation in TA100.
Colony Countinq
The revertant colonies were counted either manually or using an Artek automatic colony counter, Model 880. The counter is calibrated periodically by using computer-generated "artificial plates" consisting of a specified number of randomly placed dots within a circle the size of a petri dish. Transparencies of the "artificial plates" are counted in the same manner as a routine bacterial plate. A correction factor was determined to compensate for the area not scanned by the counter (i.e., dish edge) and overlapping colonies. This correction factor was used to automatically adjust the observed number of colonies on each plate to more accurately reflect the actual number of colonies present. - Evaluation criteria:
- Overtly toxic concentrations of the test chemical are easily visualized as showing no bacterial growth on the plate (i.e., absence of background lawn). Lower levels of toxicity may be seen as a thin or sparse bacterial lawn, a reduction in the number of revertants, or the appearance of microcolonies (overgrown background lawn). Positive and negative controls are run concurrently with the test chemical, and appropriate responses for these controls are prerequisites for evaluating the response of the bacteria to the test chemical.
A test chemical is considered a bacterial mutagen if it induces a reproducible 3-fold or higher increase in reversion frequency at more than one concentration tested. Test materials failing to meet the above criteria are considered non-mutagenic in this assay.
Results and discussion
Test results
- Species / strain:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- Toxicity was noted at 166.7, 500.0, 1667.0 and 5000.0 µg/plate with activation. Therefore, the maximum dose tested without activation was 50.0 µg/plate and with activation was 166.7 µ/plate.
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- The test material was initially assayed in TA100 at concentrations of 5.0, 16.67, 50.0, 166.7, 500.0, 1667.0, and 5000.0 µg/plate.
In this assay, the test material showed toxicity at dose levels 50.0, 166.7, 500.0, 1667.0 and 5000.0 µg/plate without activation. Toxicity was noted at 166.7, 500.0, 1667.0 and 5000.0 µg/plate with activation. Therefore, the maximum dose tested without activation was 50.0 µg/plate and with activation was 166.7 µ/plate.
There was no indication of mutagenic activity for the test chemical in any of the bacterial strains employed. The adequacy of the experimental conditions for detecting known mutagens was ascertained by employing positive control chemicals. The reversion rates observed on the solvent control plates were consistent with recent laboratory values and were representative of values observed on plates containing Oxoid L-11 agar,
The concentrations of the dose solutions used for both assays were verified analytically and found to be comparable to the targeted concentrations.
Based upon the results of this study, it is concluded that the test material did not exhibit mutagenic activity in the Ames test under the experimental conditions used. - Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative
Based upon the results of this study, it is concluded that the test material did not exhibit mutagenic activity in the Ames test under the experimental conditions used. - Executive summary:
The mutagenic potential of the substance has been assessed using a GLP-compliant Ames test study conducted according to OECD 471 but with the deviation that only four bacterial strains were used. Based upon the results of this study, it is concluded that the test material did not exhibit mutagenic activity in the Ames test under the experimental conditions used.
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