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EC number: 200-663-8 | CAS number: 67-66-3
- 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 DNA damage and/or repair study
- 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
Data source
Reference
- Reference Type:
- publication
- Title:
- Use of primary cultures of human hepatocytes in toxicology studies
- Author:
- Butterworth BE, Smith-Oliver T, Earle L, Loury DJ, White RD, Doolittle DJ, Working PK, Cattley RC, Jirtle R, Michalopoulos G, & Strom S
- Year:
- 1 989
- Bibliographic source:
- Cancer Res, 49: 1075-1084
Materials and methods
- Principles of method if other than guideline:
- Butterworth et al. (1987): Mutat. Res. 189, 113-121.
Strom et al. (1982): J. Natl. Cancer Inst. 68, 771-778.
Butterworth et al. (1983): Mutat. Res. 122, 73-80.
Mirsalis et al. (1982): Environ. Mutagen. 4, 553-562.
Briefly, the hepatocytes were incubated in media containing the test chemical and 10 µci/ml [3H] thymidine. - GLP compliance:
- no
- Type of assay:
- DNA damage and repair assay, unscheduled DNA synthesis in mammalian cells in vitro
Test material
- Reference substance name:
- Chloroform
- EC Number:
- 200-663-8
- EC Name:
- Chloroform
- Cas Number:
- 67-66-3
- Molecular formula:
- CHCl3
- IUPAC Name:
- trichloromethane
- Details on test material:
- Test substance: chloroform
Source: Fischer (Raleigh, NC)
Batch: no data
Purity: ACS certified
Constituent 1
Method
Species / strain
- Species / strain / cell type:
- primary culture, other: human hepatocytes
- Details on mammalian cell type (if applicable):
- Fresh human tissue was obtained as excess material from prescribed surgery. Small portions of apparently healthy tissue not need for pathological examination were used. Catheters were inserted in the larger vesselson the cut surface, the tissue was perfused with collagenase solution, and a primary hepatocyte culture was established.
- Additional strain / cell type characteristics:
- not applicable
- Metabolic activation:
- without
- Metabolic activation system:
- not applicable
- Test concentrations with justification for top dose:
- 0, 0.01, 0.1 and 1.0 mM
- Vehicle / solvent:
- DMSO (1 %) added to 10 uCi/mL [3H]-thymidine
Controlsopen allclose all
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- Remarks:
- 1 % DMSO
- True negative controls:
- yes
- Positive controls:
- no
- Positive control substance:
- no
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- no
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: 2-acetylamino-fluorene (2-AAF), Aflatoxin B1, 2-aminobenzyl alcohol (2-ABA), Benzo(a)pyrene, Dimethylnitrosamine (DMN)
- Details on test system and experimental conditions:
- Human Hepatocyte Preparation: Fresh human tissue was obtained as excess material from prescribed surgery. Small portions of apparently healthy tissue not needed for pathological examination were placed in ice cold saline and transported to the laboratory. Catheters were inserted in the larger vessels on the cut surface, the tissue was perfused with a collagenase solution, and a primary hepatocyte culture was established as described previously (Strom et al., (1982) J.Natl. Cancer Inst., 68, 771-778). UDS Experiments: Induction of DNA repair in the human cultures was performed as described previously (Butterworth et al. (1983) Mut. Res., 122, 73-80). Briefly, the hepatocytes were incubated in media containing the test chemical and 10 µCi/ml [3H]thymidine.
Autoradiography and Evaluation of Results: Slides were air dried, dipped in NTB 2 photographic emulsion (Kodak, Rochester, NY) diluted 1:1 with water and exposed for 8 days at 20°C. Slides were developed and scored. Silver grains over the nucleus minus the grains over an equal sized area in the cytoplasm was defined as net grains per nucleus and quantitated with an automatic grain counter. A negative number indicates there were more grains per unit area in the cytoplasm than in the nucleus. As a conservative estimate, any individual cell with greater than or equal to 5 NG was considered in repair. The percentage of cells in repair was also calculated as an indication of the extent of the response among the cells. Historical observations with rat hepatocytes indicate that if a chemical induces greater than or equal to 5 NG (population average) and greater than or equal to 20% of cells in repair, the response can be considered positive. A population average between 0 NG and 5 NG would be considered a marginal response. Because human samples differ so much from each other it was not possible to establish tight historical controls or strict criteria to define a positive response. Control cells from the same preparation do represent a true concurrent control. - Evaluation criteria:
- Any individual cell with greater than or equal to 5 NG was considered in repair. The percentage of cells in repair was also calculated as an indication of the extent of the response among the cells. Historical observations with rat hepatocytes indicate that if a chemical induces greater than or equal to 5 NG (population average) and greater than or equal to 20 % of cells in repair, the response can be considered positive.
- Statistics:
- Control cells from the same preparation do represent a true concurrent control. The unpaired t test for the equality of two means with the NG counts (population average) of the individual slides as the unit of measure is an appropriate statistical test for these data.
Results and discussion
Test results
- Key result
- Species / strain:
- other: human hepatocytes
- Metabolic activation:
- without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- not specified
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- NG values for media control were -5.5 +/- 5.1 (case 12), -1.0 +/- 4.3 (case 13) and -6.4 +/- 5.7 (case 14); NG values for solvent control (1 % DMSO) were -2.7 +/- 4.7, -0.3 +/- 4.4, and -5.8 +/- 4.4, respectively. NG values resulting from exposure to chloroform of case 12 at 0.1-1.0 mM ranged from -4.8 to -6.8, NG values resulting from exposure to chloroform of case 13 at 0.01-1.0 mM ranged from -0.1 to -1.8, and NG values resulting from exposure to chloroform of case 14 at 0.01-1.0 mM ranged from -5.5 to -9.8. NG values resulting from exposure to DMN at 0.01 to 1.0 mM of cas 12, 13 and 14 ranged from 2.8 to 31.6, 17.2 to 30.8 and from 20.1 to 26.1, respectively.
- Remarks on result:
- other: all strains/cell types tested
Any other information on results incl. tables
Table 1: DNA repair response
Chemical |
Concentration (mM) |
Case 12 |
Case 13 |
Case 14 |
Case 15 |
||||
-- |
-- |
NG ± SD a) |
%IR b) |
NG ± SD a) |
%IR b) |
NG ± SD a) |
%IR b) |
NG ± SD a) |
%IR b) |
Media control |
-- |
-5.5 ± 5.1 |
2 |
-1.0 ± 4.3 |
8 |
-6.4 ± 5.7 |
2 |
-3.9 ± 3.9 |
0 |
Solvent control |
1 % DMSO |
-2.7 ± 4.7 |
3 |
-0.3 ± 4.4 |
12 |
-5.8 ± 4.4 |
1 |
-4.1 ± 5.5 |
5 |
2-AAF |
0.001 |
-- |
-- |
21.6 ± 11.3 c) |
99 |
1.3 ± 7.4 c) |
32 |
-1.2 ± 3.6 |
5 |
0.01 |
-- |
-- |
33.3 ± 15 c) |
99 |
5.6 ± 7.8 c) |
47 |
0.9 ± 3.9 c) |
15 |
|
0.1 |
28.8 ± 12.1 c) |
100 |
33.0 ± 11.2 c) |
100 |
2.8 ± 7.7 c) |
39 |
Toxic e) |
-- |
|
Aflatoxin B1 |
0.0001 |
12.3 ± 16.7 c) |
60 |
15.6 ± 9.0 c) |
88 |
16.4 ± 9.3 c ) |
91 |
5.9 ± 8.0 c) |
54 |
0.001 |
9.1 ± 13.4 c) |
58 |
24.9 ± 13.1 c) |
97 |
59.5 ± 21.0 c) |
100 |
12.3 ± 6.4 c) |
91 |
|
0.01 |
31.0 ± 11.9 c) |
100 |
34.6 ± 16.3 c) |
99 |
61.8 ± 20.4 c) |
100 |
129.7 ± 74.7 c) |
100 |
|
2-ABA |
0.01 |
33.5 ± 14.5 c) |
100 |
64.8 ± 21.6 c) |
100 |
7.0 ± 8.7 c) |
57 |
-- |
-- |
0.1 |
25.0 ± 9.7 c) |
99 |
63.8 ± 30.8 c) |
100 |
89.8 ± 30.4 c) |
100 |
-- |
-- |
|
1.0 |
50.7 ± 19.3 c) |
100 |
56.6 ± 18.6 c) |
100 |
94.9 ± 35.6 c) |
100 |
-- |
-- |
|
Benzo(a)pyrene |
0.001 |
-- |
-- |
11.5 ± 6.7 c) |
87 |
18.7 ± 9.4 c) |
94 |
Toxic f) |
-- |
0.01 |
-- |
-- |
21.6 ± 11.4 c) |
95 |
11.8 ± 8.8 c) |
83 |
Toxic f) |
-- |
|
0.1 d) |
-- |
-- |
18.5 ± 9.1 c) |
98 |
26.5 ± 11.6 c) |
97 |
8.6 ± 12.7 c) |
70 |
|
DMN |
0.1 |
2.8 ± 7.1 c) |
37 |
17.2 ± 9.3 c) |
94 |
20.1 ± 10.3 c) |
97 |
15.5 ± 18.0 c) |
78 |
1.0 |
27.8 ± 13.8 c) |
96 |
33.2 ± 14.9 c) |
99 |
24.2 ± 13.7 c) |
96 |
53.8 ± 35.3 c) |
91 |
|
10 |
31.6 ± 17.9 c) |
93 |
30.8 ± 13.3 c) |
98 |
26.1 ± 13.4 c) |
95 |
42.2 ± 19.5 c) |
100 |
|
Chloroform |
0.01 |
-- |
-- |
-1.8 ± 4.3 |
5 |
-5.5 ± 4.2 |
1 |
-2.1 ± 3.7 |
5 |
0.1 |
-4.8 ± 5.0 |
3 |
-0.4 ± 3.5 |
6 |
-8.0 ± 7.5 |
1 |
-2.3 ± 3.8 |
3 |
|
1.0 |
-6.8 ± 5.3 |
1 |
-0.1 ± 3.3 |
5 |
-9.8 ± 7.4 |
1 |
-3.1 ± 4.2 |
1 |
a) One hundred fifty cells were counted on one slide. SD is cell-to-cell variation; b) An individual cell with ≥ 5 NG was considered in repair (IR); c) Greater than the average of the cells on the solvent control slide by the unpaired t test for the equality of two means at p ≤ 0.05; d) Solubility exceeded; e) Difficult to evaluate because cytoplasms were missing; f) Cells pyknotic and sparse with few grains.
Applicant's summary and conclusion
- Conclusions:
- In the in vitro DNA damage and repair assay (unscheduled DNA synthesis) in human hepatocytes, there was a negative response after exposure to chloroform at 0.01, 0.1 and 1.0 mM.
- Executive summary:
A test of induction of DNA repair in human hepatocytes was performed with chloroform at concentrations of 0.01, 0.1 and 1.0 mmol. None of the tested concentrations produced a genotoxic response in the human hepatocytes. Positive controls, in contrast, produced a positive response in the human hepatocytes and therefore the test was considered as valid. In the in vitro DNA damage and repair assay (unscheduled DNA synthesis) in human hepatocytes, there was a negative response after exposure to chloroform at 0.01, 0.1 and 1.0 mM. Chloroform was not mutagenic in this in vitro assay.
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