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: 200-893-9 | CAS number: 75-71-8
- 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
In all studies the results were negative with and without metabolic activation.
Link to relevant study records
- Endpoint:
- in vitro gene mutation study in mammalian cells
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 01 March 1979 to 03 May 1979
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- test procedure in accordance with national standard methods
- Remarks:
- Study report, not conducted to GLP but well documented with methodology and results included.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EPA OPPTS 870.5300 - In vitro Mammalian Cell Gene Mutation Test
- Version / remarks:
- Not specified
- Deviations:
- no
- Principles of method if other than guideline:
- See below under "details of test system and conditions"
- GLP compliance:
- not specified
- Type of assay:
- in vitro mammalian cell gene mutation test using the Hprt and xprt genes
- Target gene:
- The Chinese Hamster Ovary (CHO) cell line is used to detect mutations in a gene coding for the enzyme hypoxanthine-guanine phosphoribosyl transderase (HGPRT).
- Species / strain / cell type:
- Chinese hamster Ovary (CHO)
- Details on mammalian cell type (if applicable):
- The cells were shown to be free of mycoplasma.
- Additional strain / cell type characteristics:
- other: performed with the BH4 clone of the CHO-K1 cell line.
- Metabolic activation:
- with and without
- Metabolic activation system:
- Aroclor 1254 induced rat liver, S-9 fraction
- Test concentrations with justification for top dose:
- 0 - 51 %
- Vehicle / solvent:
- Air for test substance
- Untreated negative controls:
- not specified
- Negative solvent / vehicle controls:
- yes
- Remarks:
- Air, and respective solvents for positive controls
- True negative controls:
- yes
- Remarks:
- Air
- Positive controls:
- yes
- Positive control substance:
- other: FC-31, chlorofluoromethane; VC1, chloroethane
- Details on test system and experimental conditions:
- Cell Culture
This study was performed with the BH4 clone of the CHO-K1 cell line. Cells were routinely cultured as monolayers in Han’s F12 medium without hypoxanthine (F12 (w/o hx)) containing 10% dialyzed heat-inactivated fetal calf serum (DHIFCS). In experiments, the culture medium also contained penicillin (50 untis/ml) and streptomycin (50 micrograms/ml). Culture dishes were incubated at 37°C in an atmosphere containing 5% CO2 and 90+% relative humidity. Prior to subculturing, the cells were removed from the dishes with 0.05% trypsin. The cells were shown to be free of mycoplasma.
Activation System
Source of Liver: Livers were obtained from 8 to 9 week old male rats (Charles River CD) given Aroclor 1254 (500 mg/kg) 5 days before sacrifice. The rats were starved for the 24hr preceding sacrifice.
Preparation of Liver Homogenate: Rats were decapitated and bled. Livers from at least 6 rats were homogenized (for 5 sec) in a Waring Blender with 1.5 volumes of 0.115 M KCI at 4°C and then with a Dounce homogenizer (5 strokes). The homogenate was centrifuged under the same conditions and the resulting S-9 was stored in liquid nitrogen vapour. The concentration of protein in the S-9 was determined.
Treatment Medium
Without Activation: The treatment medium (3 ml) contained F12 (w/o hx), 10% DHIFCS, penicillin (50 units/ml), streptomycin (50 micrograms/ml), and HEPES buffer, pH 7.2 (2.5 x 10E-2M).
With Activation: The treatment medium (3 ml) contained F12 (w/o hx), S-9 (3 mg protein, unless otherwise specified), penicillin (50 units/ml), streptomycin (50 micrograms/ml), HEPES buffer, pH 7.2 (2.5 x 10-2M) MgCL2 (5.5 x 10-3M), glucose-6-phosphate (5.0 x 10E-3M), NADP (1.5 x 10E-3M), and NADH (1 x 10E-3M).
Experimental Design
Preliminary cytotoxicity experiments, with and without activation, were conducted to establish appropriate test sample concentrations for the mutagenesis experiments. Ideally, the highest concentration of test chemical should give about 10% of control survival. In each mutagenesis experiment duplicate treatments were made for each test concentration. Two or more experiments were performed with and without activation. Each experiment included a positive and solvent control.
Mutagenesis Assays
Five x 10E-5 cells were plated per 25 cm2 flask in 5 ml of culture medium. The next day the culture medium was removed and the treatment medium was added. The treatment flasks were flushed with different test gas-air mixtures. An amount of test gas-air mixture equivalent to 10 volumes of the treatment flask was flushed through each flask at a rate of about 500 ml/min. Control flasks were flushed with air. A pair of flow meters was used to generate the test gas-air mixtures. The cells were incubated for 18-19 hr (without activation) and 5 hr (with activation). Treatment flasks were incubated on a rocker panel to maximize the contact between cells and test chemical. After incubation, the flasks were flushed with air, the treatment medium was removed and the flasks were washed with culture medium. Cells treated with activation were subcultured immediately after treatment and the cells treated with activation were incubated in culture medium for 21-26 hr before subculturing.
At the time of subculturing, one portion of the cells was plated tyo assess cytotoxicity and another portion plated to allow expression of mutants resistamt to 6-thioguanine (6-TG). To assess cytotoxicity, 200 cells were plated per 60 mm dish (6 dishes) from each flask of cells in the experiment. These dishes were incubated for 7 days and the colonies were stained and counted. Cell survival was determined by dividing the total number of colonies by the total number of cells plated and was expressed both as the percent plated and as the percent of the solvent control survival.
To allow expression of the 6-TG resistant phenotype, cells from each treatment flask were plated at 1 x 10E-6 / 100 mm dish (1 dish). These cells were maintained in exponential growth for 7 days by subculturing twice (2 days after the initial subculturing and then three days later of vice versa). On the 7 th day the cells were plated to assess the cell survival and the frequency of 6-TG-resitant cells, 2 x 10E5 cells were plated per 100 mm dish (5 dishes) in culture medium containing 1 x 10-5M 6-TG. The cells were incubated for 7 days and the colonies stained and counted. The mutation frequency was expressed as the number of mutant colonies/10-6 surviving cells at the time of mutant selection. - Evaluation criteria:
- The following guidelines are used to classify a test sample as a mutagen or nonmutagen in the assay.
A test sample is classified as a nonmutagen when:
A. The probability is greater than 0.05 that the numbers of mutants at each of the test sample concentrations studies are not greater than the number of mutants in the solvent control.
AND
B. The probability is greater than 0.05 that there is not a positive correlation between the numbers of mutants and increasing concentrations of the test sample.
A sample is classified as a mutagen when:
A. The probability is less than 0.01 that the numbers of mutants at one or more of the test sample concentrations studied are not greater than the number of mutants in the solvent control.
AND
B. The probability is less than 0.01 that there is not a positive correlations between the number of mutants and increasing concentrations of the test sample.
The samples that cannot be classified by the above criteria are dealt with on a case-by-case basis. - Statistics:
- Because of the complex nature of the experimental errors in this assay, mutation frequency data were transformed prior to analysis. The formula Y = (mutation frequency + 1)E+0.15 was used because this power transformation provided data which satisfied assumptions required for performing parametric statistical analyses. The analysis used a two variable (dose and experiment). Analysis of Variance (ANOVA) Model that allows for unequal numbers of dose points and unequal numbers of test results in each trial. In one analysis, the effect of each chemical dose was compared to the solvent control by a t-test of significance to determine whether a dose caused a significant increase in the mutation frequency. The second analysis was an ANOVA to evaluate a dose-response relationship. Linear, quadratic and higher order effects were tested by an F-test of significance.
- Key result
- Species / strain:
- Chinese hamster Ovary (CHO)
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- The test chemical, dichlorodifluoromethane, was introduced into the plastic treatment flasks in the gaseous phase. An R-2-15A flow meter with a stainless steel float was used to deliver the test chemical into the flasks at a flow rate of 600 ml/min for one minute. Samples of the headspace of the flasks were taken and analysed by gas chromoatography (HY-FI, Model 600-D) using an SE-30 column at 70-80°C at the start of the treatment. The carrier gas, N2, was set at 30 psig and the flow rate of H2 was 23 ml/min. The peak heights obtained from the analysis of samples taken from each flask at the beginning of treatment were compared to the peak height of a standard vessel containing 20% test chemical and 80% air to give the concentrations (%) reported.
Two trials were performed without activation using 2.0 ml of treatment medium. The cells were exposed to the undiluted test chemical for one, five or eighteen hours. A cytoxicity response was not observed at any of these exposure times. The statistical analysis revealed no mutagenic activity according to the guidelines stated.
Two trials using an activation system containing 2.0 mg S-9 protein per ml of treatment medium (2.0 ml) were also performed. The exposure times to the undiluted test chemical were one, three and five hours. Again, no cytoxicity responses were observed. The statistical analysis using hours of exposure as the concentration showed no points to have a significant increase in the number of mutants over the solvent control and a linear dose response was not observed. The Dose X Trial Interaction suggested that the dose-response relationship in the two trials was significantly different ( p = 0.0221). When each trial was analyzed separately no significant points or linear dose responses were observed. - Conclusions:
- negative with and without metabolic activation
Dichlorodifluoromethane was tested for mutagenic activity in the Chinese Hamster Ovary Cell Assay with and without activation system. The chemical did not exhibit mutagenic activity. - Executive summary:
The Chinese Hamster Ovary (CHO) cell line is used to detect mutations in a gene coding for the enzyme hypoxanthine-guanine phosphoribosyl transferase (HGPRT). A chemical is tested for mutagenic activity on both the presence and absence of an activation system. The activation system contains rat liver homogenate and is a necessary treatment condition because CHO cells lack the ability to metabolize many carcinogens and mutagens to an active form. After treatment, the cells go through a recovery period called expression time. HGPRT deficient mutants among the surviving cells are identified by using culture medium that only allows the mutant cells to grow. The number of HGPRT deficient mutants in the treated sample compared to the number in the solvent control is the measure of mutagenic activity. A dose-response relationship is sought for chemicals displaying mutagenic activity.
RESULTS
The test chemical, dichlorodifluoromethane, was introduced into the plastic treatment flasks in the gaseous phase. An R-2-15A flow meter with a stainless steel float was used to deliver the test chemical into the flasks at a flow rate of 600 ml/min for one minute. Samples of the headspace of the flasks were taken and analysed by gas chromoatography (HY-FI, Model 600-D) using an SE-30 column at 70-80°C at the start of the treatment. The carrier gas, N2, was set at 30 psig and the flow rate of H2 was 23 ml/min. The peak heights obtained from the analysis of samples taken from each flask at the beginning of treatment were compared to the peak height of a standard vessel containing 20% test chemical and 80% air to give the concentrations (%) reported.
Two trials were performed without activation using 2.0 ml of treatment medium. The cells were exposed to the undiluted test chemical for one, five or eighteen hours. A cytoxicity response was not observed at any of these exposure times. The statistical analysis revealed no mutagenic activity according to the guidelines stated.
Two trials using an activation system containing 2.0 mg S-9 protein per ml of treatment medium (2.0 ml) were also performed. The exposure times to the undiluted test chemical were one, three and five hours. Again, no cytoxicity responses were observed. The statistical analysis using hours of exposure as the concentration showed no points to have a significant increase in the number of mutants over the solvent control and a linear dose response was not observed. The Dose X Trial Interaction suggested that the dose-response relationship in the two trials was significantly different ( p = 0.0221). When each trial was analyzed separately no significant points or linear dose responses were observed.
CONCLUSIONS
Dichlorodifluoromethane was tested for mutagenic activity in the Chinese Hamster Ovary Cell Assay with and without activation system. The chemical did not exhibit mutagenic activity.
Reference
TABLE I – TOXICITY AND MUTAGENCITY OF H-12,830 IN CHINESE HAMSTER OVARY CELLS WITHOUT ACTIVATION – TRIAL ONE
Compound |
Concentration (%) |
Cells/flasks** (x 106) |
TOXICITY |
MUTAGENICITY |
|||
Cell Survival |
Cell Survival (% Plated) |
Mutants |
|||||
(% Plated) |
(% Control) |
Total |
Frequency* |
||||
12,830 |
0 (a) |
3.93 |
59.8 |
100 |
77.8 |
7 |
9.0 |
“ |
42 (a) 44 (a) |
3.86 3.61 |
58.2 59.8 |
97.3 100.0 |
77.4 80.7 |
4 1 |
5.2 1.2 |
“ |
0 (b) 0 (b) |
3.95 3.74 |
65.1 66.9 |
100+ |
79.8 75.0 |
0 5 |
0 6.7 |
“ |
40 (b) 42 (b) |
3.55 3.63 |
58.2 67.8 |
88.2 102.7 |
68.1 77.4 |
3 0 |
4.4 0 |
“ |
0 (c) 0 (c) |
2.88 2.95 |
0 60.6 |
100+ |
64.8 72.2 |
5 1 |
7.7 1.4 |
“ |
42 (c) 40 (c) |
2.95 2.88 |
63.7 61.6 |
104.6 101.1 |
67.8 70.0 |
4 4 |
5.9 5.7 |
FC-31 |
++ (a) |
3.42 |
50.2 |
83.9 |
67.8 |
42 |
61.9 |
(a) One hour exposure
(b) Five hour exposure
(c) Eighteen hour exposure
12,830 = Dichlorodifluoromethane
TABLE II – TOXICITY AND MUTAGENICITY OF H-12,830 IN CHINESE HAMSTER OVARY CELLS WITHOUT ACTIVATION – TRIAL TWO
Compound |
Concentration (%) |
Cells/flasks** (x 106) |
TOXICITY |
MUTAGENICITY |
|||
Cell Survival |
Cell Survival (% Plated) |
Mutants |
|||||
(% Plated) |
(% Control) |
Total |
Frequency* |
||||
12,830 |
0 (a) |
3.57 |
65.6 |
100 |
78.8 |
6 |
7.6 |
“ |
49 (a) 49 (a) |
3.71 3.77 |
71.8 60.1 |
109.5 91.6 |
85.2 89.0 |
2 3 |
2.3 3.4 |
“ |
0 (b) 0 (b) |
3.92 3.74 |
63.2 70.7 |
100+ |
89.5 85.6 |
6 7 |
6.7 8.2 |
“ |
49 (b) 49 (b) |
3.79 3.78 |
55.9 60.9 |
83.4 90.9 |
89.3 89.0 |
21 1 |
23.5 1.1 |
“ |
0 (c) 0 (c) |
3.09 2.92 |
60.2 61.2 |
100+ |
91.2 88.8 |
3 4 |
3.3 4.5 |
“ |
46 (c) 43 (c) |
2.49 2.63 |
66.3 72.9 |
109.2 120.1 |
76.9 72.2 |
11 4 |
14.3 5.5 |
FC-31 |
++ (a) |
2.81 |
39.4 |
60.1 |
59.8 |
21 |
35.1 |
(a) One hour exposure
(b) Five hour exposure
(c) Eighteen hour expousre
12,830 = Dichlorodifluoromethane
TABLE III – TOXICITY AND MUTAGENICITY OF H-12,830 IN CHINESE HAMSTER OVARY CELLS WITH ACTIVATION – TRIAL ONE
Compound |
Concentration (%) |
Cells/flasks** (x 106) |
TOXICITY |
MUTAGENICITY |
|||
Cell Survival |
Cell Survival (% Plated) |
Mutants |
|||||
(% Plated) |
(% Control) |
Total |
Frequency* |
||||
12,830 |
0 (a) 0 (a) |
2.49 2.84 |
62.5 55.1 |
100+ |
83.7 79.0 |
7 8 |
8.4 10.1 |
“ |
44 (a) 44 (a) |
2.83 2.80 |
64.9 63.4 |
110.4 107.4 |
79.1 73.8 |
3 5 |
3.8 6.8 |
“ |
0 (b) 0 (b) |
2.10 2.18 |
61.2 56.4 |
100+ |
80.1 77.6 |
3 19 |
3.7 24.5 |
“ |
36 (b) 40 (b) |
2.39 2.05 |
54.8 56.3 |
93.2 95.7 |
72.7 70.8 |
4 10 |
5.5 14.1 |
“ |
0 (c) 0 (c) |
1.83 1.45 |
57.5 59.1 |
100+ |
59.4 74.3 |
7 14 |
11.8 18.8 |
“ |
44 (c) 42 (c) |
2.43 2.02 |
67.4 62.8 |
115.6 107.7 |
78.2 78.2 |
1 0 |
1.3 0 |
VC1 |
†† (a) †† (a) |
1.34 1.46 |
34.0 30.2 |
57.8 51.4 |
50.4 45.2 |
195 118 |
386.9 261.1 |
(a) One hour exposure
(b) Three hour exposure
(c) Five hour exposure
12,830 = Dichlorodifluoromethane
TABLE IV – TOXICITY AND MUTAGENICITY OF H-12,830 IN CHINESE HAMSTER OVARY CELLS WITH ACTIVATION – TRIAL TWO
Compound |
Concentration (%) |
Cells/flask** (x 106) |
TOXICITY |
MUTAGENICITY |
|||
Cell Survival |
Cell Survival (% Plated) |
Mutants |
|||||
(% Plated) |
(% control) |
Total |
Frequency* |
||||
12,830 |
0 (a) |
2.42 |
74.2 |
100 |
94.2 |
20 |
21.2 |
“ |
51 (a) 51 (a) |
2.61 2.72 |
67.2 57.1 |
90.6 77.0 |
90.2 94.3 |
11 0 |
12.2 0 |
“ |
0 (b) 0 (b) |
2.08 2.00 |
68.6 67.3 |
100+ |
89.4 92.4 |
16 17 |
17.9 18.4 |
“ |
44 (b) 48 (b) |
2.41 2.46 |
64.2 62.1 |
94.4 91.3 |
84.7 89.7 |
3 2 |
3.5 2.2 |
“ |
0 (c) 0 (c) |
1.68 1.57 |
66.3 68.9 |
100+ |
100.7 91.5 |
2 2 |
2.0 (d) 2.2 |
“ |
47 (c) 48 (c) |
2.16 2.34 |
64.5 69.8 |
95.4 103.3 |
90.5 80.3 |
18 8 |
19.9 10.0 |
VC1 |
†† (a) |
1.41 |
43.6 |
58.8 |
84.2 |
179 |
212.6 |
(a) One hour exposure
(b) Three hour exposure
(c) Five hour exposure
(d) A cell survival of 100% was used to calculate mutant frequency
12,830 = Dichlorodifluoromethane
Symbols:
(*) Mutants per 106surviving cells
(**) Cells per flask at the time of the initial subculturing
(+) The average of the duplicate plating efficiencies was set equal to 100%
(†) Computed from the average transformed mutation frequency, Y.
(††) 100% VC1 in the gaseous phase was introduced into the treatment flasks for one minute.
(NF) None found
(++) A mixture of two thirds FC-31 and one third air was introduced into the treatment flasks for one minute.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Genetic toxicity in vivo
Description of key information
Results of a Rat Dominant Lethal Assay are reported as part of a reproduction study. No effects were observed.
Link to relevant study records
- Endpoint:
- in vivo mammalian germ cell study: cytogenicity / chromosome aberration
- Remarks:
- Dominant Lethal Assay/chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Reason / purpose for cross-reference:
- reference to same study
- Principles of method if other than guideline:
- - Principle of test:
Dominant Lethal assay, part of a reproductive toxicity study.
- Short description of test conditions: The F0 animals of the reproduction study were mated to initiate an F1b litter. Animals were treated with the test substance gavage until pregnancies were terminated in mid-term to give a dominant lethal assay
- Parameters analysed / observed: fetal mortality - GLP compliance:
- not specified
- Remarks:
- Not likely (prior to GLP standards)
- Type of assay:
- rodent dominant lethal assay
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on species / strain selection:
- Charles River CD
- Sex:
- male/female
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle used: corn oil
- Duration of treatment / exposure:
- F0 animals were mater to initiate an F1b litter. Animals were treated by gavage until pregnancies were terminated in mid-term to give a dominant lethal assay.
- Frequency of treatment:
- Daily treatment for several weeks (no other details)
- Dose / conc.:
- 15 mg/kg bw/day
- Remarks:
- (or 0.2%)
- Dose / conc.:
- 150 mg/kg bw/day
- Remarks:
- (or 2%)
- No. of animals per sex per dose:
- no data
- Control animals:
- not specified
- Evaluation criteria:
- fetal mortality
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Conclusions:
- There was no evidence of adverse effects in the Dominant lethal assay, indicating that the substance did not cause chromosome damage to germ cells of the treated male rats.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Additional information
The substance was negative in the following tests:
1) Bacterial reverse mutation assay (e.g. Ames test) – 3 separate studies.
2) Gene mutation - Cell transformation (Styles) assay
3) Rat Dominant Lethal Assay (included as part of a reproduction study)
4) in vitro gene mutation in mammalian cells - CHO/HGPRT – 2 separate studies
Three separate bacterial reverse mutation tests showed that the substance does not have any mutagenic properties in different Salmonella strains and E. Coli strains. In addition, no genotoxic properties have been seen in in-vitro gene mutation nor in an in-vitro Cell transformation (Styles) assay. The rat Dominant Lethal assay indicated no chromosome damage on germ cells. Repeated-dose studies and carcinogenicity studies by inhalation treatment in rats, mice and dogs did not reveal any tumorigenic properties which could be related to the administration of the test substance.
Justification for classification or non-classification
The above studies have all been ranked reliability 2 according to the Klimish et al system. This ranking was deemed appropriate because the studies were not conducted to GLP and are not in compliance with agreed protocols. However these are considered appropriate for use in assessment purposes in accordance with the criteria listed in Annex XI. As such, it is deemed appropriate to apply a weight of evidence approach based on similarity and animal welfare grounds.
The above results triggered no classification under the criteria of the CLP Regulation (EC No 1272/2008). No classification for mutagenic effects is therefore required.
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.
