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EC number: 208-792-1 | CAS number: 541-73-1
- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Genetic toxicity in vitro
Description of key information
OECD TG 471 (Shimazu, 1983): Not mutagenic
OECD TG 476 (Wollny, 2015): Not mutagenic
The in vitro gene mutation studies conducted were not conclusive for classification due to deviations noted. Therefore the classification of the test substance required the use of an additional in vivo study. The results from the in vitro (mamalian cells) OECD TG 476 combined with the results from the in vitro study were sufficient to rule out classification of the substance as mutagenic according to the CLP Regulation (EC) No 1272/2008.
Link to relevant study records
- 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:
- comparable to guideline study with acceptable restrictions
- Remarks:
- The study deviates from the TG by not using one of the following strains E. coli WP2 uvrA, or E. coli WP2 uvrA (pKM101), or S. typhimurium TA102.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- yes
- Remarks:
- Rats were injected with PCB instead of Aroclor 1254. The S. thyphimurium strains, TA98, TA1538, TA1537, TA100 and TA 1535 were used instead of TA1535, TA1537 (or TA97a or TA97), TA98, and TA100 , and E.coli WP2 strains or S. typhimurium TA102.
- Principles of method if other than guideline:
- The mutagenicity of chlorobenzene compounds in Salmonella typhimurium (strains TA98, TA1538, TA1537, TA100 and TA1535) was examined.
- GLP compliance:
- not specified
- Type of assay:
- bacterial reverse mutation assay
- Target gene:
- his
- Species / strain / cell type:
- other: TA 98, TA 100, TA 1535, TA 1537, TA 1538
- Metabolic activation:
- with and without
- Metabolic activation system:
- S9 mix
- Test concentrations with justification for top dose:
- 0.02, 0.04, 0.08, 0.16, 0.32, 0.64, 1.28, 2.56 µL
- Vehicle / solvent:
- - Vehicle used: DMSO
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: N-Ethyl-N´-nitro-N-nitrosoguanidine (ENNG), 2-nitrofluorene (2-NF), 9-aminoacridine (9-AA) and 2-aminoanthracene (2-AA)
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: preincubation
NUMBER OF REPLICATIONS: all test were performed in duplicate and repeated at least 3 times - Evaluation criteria:
- Colonies of his+ revertants were counted after incubation, and chemicals inducing more than twice the number of revertant colonies on the control plate were considered as mutagenic.
- Statistics:
- Not performed
- Species / strain:
- S. typhimurium TA 1538
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- True negative controls validity:
- valid
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 1537
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- True negative controls validity:
- valid
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 1535
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- True negative controls validity:
- valid
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Vehicle controls validity:
- valid
- True negative controls validity:
- valid
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 98
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'. Remarks: TA 98, TA 100, TA 1535, TA 1537, TA 1538
- Conclusions:
- Under the conditions of the study, the test item was not mutagenic and not classified according to CLP Regulation (EC) 1272/2008.
- Executive summary:
The mutagenicity of 1,3-dichlorobenzene was examined in Salmonella typhimurium (strains TA98, TA, 1538, TA 1537, TA 100, and TA 1535). The test was carried out with and without liver microsomal activation.
1,3-dichlorobenzene showed no mutagenic activity and toxicity at higher doses.
- Endpoint:
- in vitro gene mutation study in mammalian cells
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 476 (In Vitro Mammalian Cell Gene Mutation Test)
- Principles of method if other than guideline:
- This in vitro assay was performed to assess the potential of 1,3-dichlorobenzene to induce gene mutations by means of two independent HPRT experiments using the Chinese hamster cell line V79. The treatment time was 4 hours in the first experiment with and without metabolic activation. In the second experiment the cells were exposed to the test item for 24 hours without metabolic activation and 4 hours with metabolic activation.
- GLP compliance:
- yes
- Type of assay:
- mammalian cell gene mutation assay
- Target gene:
- HPRT locus
- Species / strain / cell type:
- Chinese hamster lung fibroblasts (V79)
- Additional strain / cell type characteristics:
- other: the cells have a stable karyothype with a modal chromosome number of 22
- Metabolic activation:
- with and without
- Metabolic activation system:
- S9 mix
- Test concentrations with justification for top dose:
- exposure S9
period mix
concentrations in µg/mL
Experiment I
4 hours - 5.9 11.8 23.5 47.0 94.0 188.0
4 hours + 5.9 11.8 23.5 47.0 94.0 188.0
Experiment II
24 hours - 5.9 11.8 23.5 47.0 94.0 141.0
4 hours + 5.9 11.8 23.5 47.0 70.5 94.0 - Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- not specified
- Positive controls:
- yes
- Positive control substance:
- other: Without metabolic activation: EMS; ethylmethane sulfonate; With metabolic activation: DMBA; 7,12-dimethylbenz(a)anthracene
- Species / strain:
- Chinese hamster lung fibroblasts (V79)
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- other: Relevant cytotoxic effects were observed at 187.5 µg/mL and above following 24 hours treatment without metabolic activation. No relevant cytotoxicity occurred after 4h treatment with and without metabolic activation.
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Remarks on result:
- other: other: Chinese hamster lung fibroblasts (V79)
- Remarks:
- Migrated from field 'Test system'.
- Conclusions:
- Under the conditions of this study , the test item is not mutagentic according to CLP Regulation (EC) No. 1271/2008.
- Executive summary:
The study was performed to investigate the potential of 1,3-dichlorobenzene, CAS 541-73-1 to induce gene mutations at the HPRT locus in V79 cells of the Chinese hamster. This study was designed to be compatible with the procedures indicated by the internationally accepted guidelines and recommendations.
The assay was performed in two independent experiments. The cells were exposed to the test item for 4 hours in the first experiment with and without metabolic activation. The second experiment was performed with a treatment time of 4 hours with and 24 hours without metabolic activation.
The maximum concentration of the pre-experiment (1500 µg/mL) was equal to a molar concentration of about 10 mM. The concentration range of the main experiments was limited by cytotoxicity and phase separation of the test item in culture medium.
No substantial and reproducible dose dependent increase of the mutation frequency was observed in both main experiments.
Appropriate reference mutagens, used as positive controls, induced a distinct increase in mutant colonies and thus, showed the sensitivity of the test system and the activity of the metabolic activation system.
In conclusion it can be stated that under the experimental conditions reported the test item did not induce gene mutations at the HPRT locus in V79 cells.
Therefore, 1,3-dichlorobenzene, CAS 541-73-1 is considered to be non-mutagenic in this HPRT assay.
Referenceopen allclose all
Mutagenicity of 1,3-dichlorobenzene in S.typhimurium TA 98, TA 1538, TA 1537, TA100, and TA 1535
Dose per plate µL |
His+ revertants/plate |
|||||||||
|
TA98 |
TA 1538 |
TA 1537 |
TA 100 |
TA 1535 |
|||||
|
-S9 |
+S9 |
-S9 |
+S9 |
-S9 |
+S9 |
-S9 |
+S9 |
-S9 |
+S9 |
0.02 |
30 ± 3 |
29 ± 4 |
24 ± 4 |
24 ± 5 |
8 ± 2 |
6 ± 2 |
180 ± 22 |
228 ± 22 |
36 ± 5 |
32 ± 4 |
0.04 |
28 ± 3 |
33 ± 7 |
22 ± 3 |
18 ± 3 |
13 ± 3 |
9 ± 2 |
172 ± 16 |
196 ± 17 |
31 ± 4 |
38 ± 6 |
0.08 |
30 ± 5 |
24 ± 3 |
21 ± 3 |
22 ± 3 |
10 ± 2 |
9 ± 2 |
135 ± 25 |
190 ± 15 |
32 ± 5 |
30 ± 3 |
0.16 |
21 ± 3 |
29 ± 5 |
17 ± 2 |
30 ± 6 |
8 ± 2 |
8 ± 2 |
142 ±18 |
186 ±18 |
29 ± 4 |
24 ± 3 |
0.32 |
23 ± 4 |
22 ± 3 |
25 ± 5 |
20 ± 2 |
9 ± 2 |
11 ± 4 |
154 ± 13 |
177 ±16 |
22 ± 3 |
28 ±4 |
0.64 |
17 ± 2 |
25 ± 4 |
21 ± 4 |
31 ± 5 |
10 ± 3 |
9 ± 2 |
156 ±18 |
181 ± 17 |
28 ± 5 |
24 ± 3 |
1.28 |
15 ± 3 * |
20 ± 3 |
0* |
2± 8* |
3 ± 3* |
5 ± 3* |
155 ± 9 |
164 ±14 |
6 ± 8* |
17 ± 3 |
2.56 |
0* |
0* |
0* |
0* |
0* |
0* |
0* |
42 ±22* |
0* |
0* |
The test item 1,3-dichlorobenzene, CAS 541-73-1 was assessed for its potential to induce gene mutations at the HPRT locus using V79 cells of the Chinese hamster.
The study was performed in two independent experiments, using identical general experimental procedures.
In the first experiment the treatment period was 4 hours with and without metabolic activation. The second experiment was performed with a treatment time of 4 hours with and 24 hours without metabolic activation.
The main experiments were evaluated at the following concentrations:
exposure S9
period mix
concentrations in µg/mL
Experiment I
4 hours - 11.8 23.5 47.0 94.0 188.0
4 hours + 5.9 11.8 23.5 47.0 94.0
Experiment II
24 hours - 5.9 11.8 23.5 47.0 94.0
4 hours + 11.8 23.5 47.0 70.5 94.0
Phase separation occurred in experiment I at 94.0 µg/mL and above without metabolic activation and at 94.0 µg/mL with metabolic activation. In experiment II phase separation was observed at 94.0 µg/mL and above with and without metabolic activation.
Relevant cytotoxic effects, indicated by a relative cloning efficiency I or a relative cell density at first subcultivation of less than 50% in both parallel cultures, occurred in the first experiment at 94.0 µg/mL and above with and without metabolic activation. In the second experiment relevant cytotoxic effects as described above were noted at 94 µg/mL with metabolic activation. The maximum concentration of the second experiment without metabolic activation was limited by phase separation. The recommended cytotoxic range of approximately 10%-20% relative cloning efficiency or relative cell density was covered with and without metabolic activation. Compared to the pre-experiment, cytotoxicity occurred at lower concentrations in the main experiments, especially after 4 hour treatment. However, the cytotoxicity was observed at concentrations showing phase separation or at the limit of solubility. An organic phase usually is toxic on direct contact to the cells as cell membranes are damaged. As the number of cells coming into direct contact with an organic phase in culture medium is variable, cytotoxic effects in an insoluble concentration range are poorly reproducible.
No relevant and reproducible increase in mutant colony numbers/10E6 cells was observed in the main experiments up to the maximum concentration. The mutation frequency generally remained within the historical range of solvent controls. An isolated increase of the mutation frequency exceeding the threshold of three times the mutation frequency of the solvent control was noted in the first experiment, culture II with metabolic activation at 23.5 and 94.0 µg/mL. However, the threshold was not exceeded in the parallel culture or in the second experiment with metabolic activation. Consequently, the isolated increase described above was judged as biologically irrelevant.
A linear regression analysis (least squares) was performed to assess a possible dose dependent increase of mutant frequencies. A significant dose dependent trend of the mutation frequency indicated by a probability value of <0.05 was determined in the second culture of experiment I with metabolic activation. However, this increase was judged as irrelevant fluctuation as discussed above.
In both experiments of this study (with and without S9 mix) the range of the solvent controls was from 11.1 up to 33.3 mutants per 10E6 cells; the range of the groups treated with the test item was from 5.9 up to 54.6 mutants per 10E6 cells.
EMS (150 µg/mL) and DMBA (2.2 µg/mL in experiment I and 1.1 mg/mL in experiment II) were used as positive controls and showed a distinct increase in induced mutant colonies.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Additional information
Initial assessment for genetic toxicity was conducted under OECD TG 471:Bacterial Reverse Mutation Test (Shimazu, 1983). Deviations were noted in the study; the S. thyphimurium strains, TA98, TA1538, TA1537, TA100 and TA 1535 were used instead of TA1535, TA1537 (or TA97a or TA97), TA98, and TA100 , and E.coli WP2 strains or S. typhimurium TA102. The four main S. thyphimurium strains have GC base pairs at the primary reversion site and are known to have limited capacity to detect certain oxidising mutagens, cross-linking agents and hydrazines. Therefore the use of E.coli WP2 strains or S. typhimurium TA102 allow for the detection of such substances as the strains have an AT base pair at the primary reversion site.
Justification for classification or non-classification
All available valid tests were negative. Therefore a classification is not justified.
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