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EC number: 201-757-1 | CAS number: 87-61-6
- 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- publication
- Title:
- Salmonella Mutagenicity Test results for 250 Chemicals
- Author:
- Haworth S, Lawlor T, Mortelmans K, Speck W, and Zeiger E
- Year:
- 1 983
- Bibliographic source:
- Environmental Mutagenesis Supplement 1:3-142
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Version / remarks:
- 1981
- Deviations:
- yes
- Remarks:
- Only 4 strain tested instead of 5. Positive control: 2-aminoantracene was only indicator of efficiency of S9-mix. Individual plate reading not reported.
- GLP compliance:
- not specified
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- 1,2,3-trichlorobenzene
- EC Number:
- 201-757-1
- EC Name:
- 1,2,3-trichlorobenzene
- Cas Number:
- 87-61-6
- Molecular formula:
- C6H3Cl3
- IUPAC Name:
- 1,2,3-trichlorobenzene
- Test material form:
- not specified
- Details on test material:
- - Name of test material (as cited in study report): 1,2,3-Trichlorobenzene
- Analytical purity: 97%
- Lot/batch No.: HC 060787
-Source: Radian Corporation, Austin, TX, USA
Constituent 1
- Specific details on test material used for the study:
- STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: not reported
- Stability and homogeneity of the test material in the vehicle/solvent under test conditions (e.g. in the exposure medium) and during storage: not reported
- Stability in the medium, i.e. sensitivity of the test material to hydrolysis and/or photolysis: not reported
- Solubility and stability of the test material in the solvent/vehicle and the exposure medium: not reported
- Reactivity of the test material with the incubation material used (e.g. plastic ware): not reported
TREATMENT OF TEST MATERIAL PRIOR TO TESTING
- Treatment of test material prior to testing (e.g. warming, grinding): formulated in DMSO
- Final concentration of a dissolved solid, stock liquid or gel: not reported
Method
- Target gene:
- his
Species / strain
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Additional strain / cell type characteristics:
- not specified
- Metabolic activation:
- with and without
- Metabolic activation system:
- Type and composition of metabolic activation system:
- source of S9: male Sprague-Dawley rats and male Syrian hamsters that were injected, ip, with Aroclor 1254 (200 mg/ml in corn oil) at 500 mg/kg. Five days after injection, the animals were sacriftced by decapitation (EGG, SRI) or cervical dislocation (CWR) and the livers were removed aseptically, The animals were fasted for 12-24 hr immediately preceding sacrifice.
- method of preparation of S9 mix: Liver homogenates were prepared aseptically at 0-4°C. Excised livers were rinsed with 0.15 M KCl, then minced and homogenized (3 ml of 0.15 M KCI/g wet tissue) in a Potter-Elvehjem apparatus with a teflon pestle (EGG, SRI) or in a Waring blender (CWR). The homogenate was centrifuged for 10 min at 9,000g at 4°C. The supernatant (S-9) was decanted and distributed into freezing ampules and stored at
-70°C.
The microsornal enzyme reaction mix (S-9 mix) was prepared immediately prior
to each assay. Unused S-9 mix was discarded and not refrozen. One milliliter of S-9 mix has the following composition: S-9, 0.10 ml; 0.04 M MgCl2, 0.02 ml; 1.65 M KCl, 0.02 ml; 0.04 M ß-nicotinamide adenine dinucleotide phosphate (NADP), 0.10 ml; 0.05 M glucose-6-phosphate, 0.10 ml; 1.0 M NaH2P04 (pH 7.4), 0.10 ml; and distilled water, 0.56 ml.
- concentration or volume of S9 mix and S9 in the final culture medium: not reported
- quality controls of S9 (e.g., enzymatic activity, sterility, metabolic capability): not reported - Test concentrations with justification for top dose:
- 0.0, 3.3, 10.0, 33.3, 100.0, 333.3 ug/plate
- Vehicle / solvent:
- - Vehicle/solvent used: DMSO
- Justification for choice of solvent/vehicle: the chemical was not soluble in water
- Justification for percentage of solvent in the final culture medium: not reported
Controls
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- 9-aminoacridine
- sodium azide
- other: 2-aminoanthracene (2-AA) & 4-Nitro-o-phenylenediamine (NOPD)
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: preincubation
DURATION
- Preincubation period: 20 min
- Exposure duration: 48h
- Selection time (if incubation with a selection agent): 48h
- Concentration of S9 mix: 10% for both Hamster S9 mix and Rat S9 mix
SELECTION AGENT (mutation assays): L- histidine
NUMBER OF REPLICATIONS: 2 trial per strain and 3 plates per dose
DETERMINATION OF CYTOTOXICITY
- Method: other: viability on complete medium and reduced numbers of revertant colonies per plate and/or thinning or absence of the bacterial lawn - Evaluation criteria:
- A positive response was indicated by a reproducible, dose-related increase, whether it be twofold over background or not.
An equivocal response was defined as an increase in revertants which was not dose-related, not reproducible, or was of insufficient magnitude to support a determination of mutagenicity. A negative response was obtained when no increase in revertant colonies is observed following chemical treatment.
Results and discussion
Test results
- Key result
- 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
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- True negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- TEST-SPECIFIC CONFOUNDING FACTORS
- Data on pH: no effect reported
- Data on osmolality: no effect reported
- Possibility of evaporation from medium: no effect reported
- Water solubility: no effect reported
- Precipitation and time of the determination: no effect reported
RANGE-FINDING/SCREENING STUDIES (if applicable):
to select the dose range for the mutagenesis assay, the test chemicals were checked for toxicity to TA 100 up to a concentration of 10 mg/plate or the limit of solubility, both in the presence and absence of S-9 mix. If toxicity was not apparent in the preliminary toxicity determination, the highest dose tested was 10 mg/plate; otherwise the upper limit of solubility was used. If toxicity was observed, the doses of test chemical were chosen so that the high dose exhibited some degree of toxicity. Occasionally, in the earlier tests, the high dose was greater than 10 mf/plate.
STUDY RESULTS: see Table 2
HISTORICAL CONTROL DATA (with ranges, means and standard deviation, and 95% control limits for the distribution as well as the number of data)
- Positive historical control data: not reported
- Negative (solvent/vehicle) historical control data: Not reported
Any other information on results incl. tables
Table 2 Mutagenic responses of Salmonella strains TA100, TA 1535, TA 1537, and TA 98 (mean±SEM) to 1,2,3-trochlorobenzene.
| TA 100 | TA 1535 | TA 1537 | TA 98 | ||||||||
Dose | NA | RLI | HLI | NA | RLI | HLI | NA | RLI | HLI | NA | RLI | HLI |
0.0 | 124±9.9 | 138±7.0 | 131±7.3 | 25±6.0 | 12±2.9 | 14±0.9 | 11±2.7 | 20±0.3 | 26±3.5 | 25±2.4 | 22±5.0 | 35±3.4 |
3.3 | 122±13.2 | 122±9.7 | 114±4.1 | 17±1.7 | 10±2.2 | 16±2.0 | 8±2.1 | 15±3.2 | 18±3.0 | 20±3.0 | 26±2.2 | 32±1.0 |
10.0 | 134±14.0 | 131±7.5 | 122±7.2 | 20±4.6 | 14±0.3 | 13±0.3 | 12±1.3 | 14±3.5 | 22±3.0 | 16±4.8 | 24±1.7 | 31±3.2 |
33.3 | 91±3.8 | 131±11.6 | 135±10.6 | 17±2.3 | 14±2.9 | 16±1.5 | 6±1.3 | 13±3.8 | 18±1.5 | 20±0.7 | 23±3.7 | 32±5.1 |
100.0 | 11± 6.9s | 91±6.4 | 124±10.2 | 0±0.0s | 8±1.5 | 14±3.8 | 0±0.0s | 11±1.8 | 21±3.3 | 10±2.9s | 27±0.6 | 31±2.0 |
333.3 | t | t | 80±2.8s | t | 4±2.2s | 6±0.7s | t | 0±0.0s | 6±1.0s | t | 6±3.2s | 18±6.2s |
POS | 550±8.1 | 596±29.5 | 556±9.5 | 438±5.3 | 334±51.3 | 367±6.2 | 163±24.0 | 287±3.6 | 467±13.0 | 474±16.3 | 388±25.1 | 934±19.9 |
Abbreviations:NA, not activated; RLI, rat liver S-9, Aroclor1254 induced; HLI, hamster liver S-9, Aroclor1254 induced, t=complete clearing background, s=slight clearing of background lawn
Applicant's summary and conclusion
- Conclusions:
- negative with metabolic activation;
negative without metabolic activation - Executive summary:
Haworth S, 1983
Ames test was performed with theSalmonella typhimurium strains TA1535, TA1537, TA98 and TA100 at 0, 3.3, 10, 33.3, 100, and 333.3µg 1,2,3-TCB/plate with and without S-9 from Aroclor 1254 induced rat and hamster livers using the preincubation procedure. Test doses were chosen following checks for toxicity: in the absence of toxicity a maximum of 10 mg/plate was used. 1,2,3-trichlorobenzene resulted to be not mutagenic.
The test was conducted according to OECD guideline 471 with deviations (Only 4 strains tested instead of 5. Positive control: 2-aminoantracene was only indicator of efficiency of S9-mix.Individual plate reading not reported).
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