Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
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
Carcinogenicity
Administrative data
Description of key information
Results from several long-term studies were available for weight of evidence assessment: a carcinogenicity study by inhalation in rats and mice, and an oral study in rats. No tumors or adverse effects were reported.
Inhalation: Rat chronic administration: NOAEC: 5000 ppm, i.e., 24725 mg/m3
Key value for chemical safety assessment
Carcinogenicity: via oral route
Link to relevant study records
- Endpoint:
- carcinogenicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- no data
- 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
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- - Principle of test:
in a multigeneration study by the oral route, groups of 50 male and 50 female Charles River rats of the F1a generation remained in the test for 2 years, with an interim kill at 1 year. Starting at 6 weeks of age, controls, low-dose, and high-dose groups received CFC-12 in corn oil or corn oil alone daily by gavage for 6 weeks and 5 times / week thereafter
- Parameters analysed / observed: survival, periodic measurements of haematological, clinical chemistry, and urinalysis values, organ weights and histopathological findings. - GLP compliance:
- no
- Remarks:
- Prior to GLP standards
- Species:
- rat
- Strain:
- Sprague-Dawley
- Remarks:
- Charles River CD
- Sex:
- male/female
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- 2 years
- Frequency of treatment:
- daily
- Dose / conc.:
- 0 mg/kg bw/day (nominal)
- Dose / conc.:
- 15 mg/kg bw/day (nominal)
- Dose / conc.:
- 150 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 50
- Control animals:
- yes
- Details on study design:
- Multigeneration study. The rats from the F1a generation were dosed for 2 years by gavage. An interim kill of 6 rats/group was made after one year of treatment.
- Positive control:
- No
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: No data
DETAILED CLINICAL OBSERVATIONS: No data
BODY WEIGHT: Yes
- Time schedule for examinations: frequency not detailed
FOOD CONSUMPTION : No data
HAEMATOLOGY: Yes
CLINICAL CHEMISTRY: Yes
URINALYSIS: Yes
NEUROBEHAVIOURAL EXAMINATION: No data
- Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes - Clinical signs:
- no effects observed
- Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- No difference in survival between treated and control groups
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Slight decreased body weight in females of the high dose group.
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Key result
- Dose descriptor:
- NOAEC
- Effect level:
- ca. 150 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Critical effects observed:
- no
- Conclusions:
- There was no evidence of carcinogenic effects in male and female rats following a 2-year administration by oral gavage.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 150 mg/kg bw/day
- Study duration:
- chronic
- Species:
- rat
Carcinogenicity: via inhalation route
Link to relevant study records
- Endpoint:
- carcinogenicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 1975 to 1979
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- Taken from publically available data. The study is well documented and contains suitable information for use in the assessment. The full literature report is appended for reference.
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- CFC-12 was tested by inhalation on Sprague-Dawley rats and Swiss Mice using whole body exposure. The animals were exposed by inhalation, 4 hours daily, 5 days weekly, for 104 weeks (rats: Exp. BT 601, 601 bis) and 78 weeks (mice: Exp. BT 602).
All the animals were kept under control until spontaneous death. The status and behaviour of the animals were controlled three times daily. The animals were submitted to clinical examination for gross changes every 2 weeks. The animals were weighed every 2 weeks during treatment, and then every 8 weeks. Full necropsy was performed on all the animals. The housing and the diet of the animals were the same highly standardized ones adopted in the BT Experimental Unit during the last 15 years before the beginning of this experiment. - GLP compliance:
- not specified
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source of test material: Montedison, Italy
- Purity : 99.98%
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Male and female Sprague-Dawley rats 9 (Exp. BT 601), and 13 (Exp. BT 601 bis) weeks old at the start of the experiment.
The animals were of the breed currently used in the BT Experimental Unit for more than 15 years.
All the animals were kept under control until spontaneous death.
The status and behaviour of the animals were controlled three times daily.
The housing and the diet of the animals were the same highly standardized ones adopted in the BT Experimental Unit during the last 15 years before the beginning of this experiment. - Route of administration:
- inhalation
- Type of inhalation exposure (if applicable):
- whole body
- Vehicle:
- air
- Details on exposure:
- The chambers for inhalation exposure were made of stainless steel, with two glass doors, and they measure 135 x 98 x 65 cm. The volume of each chamber is 860 litres. Continuous air flow provided 12-15 air changes per hour. Before its introduction the air was filtered, and the chamber arrangement was such that air flowed from one part of the chamber to the other without recirculation. The internal pressure was about 1 mm Hg less than that of the room where the chambers were situated to avoid any possible contamination of the outside environment.
FC 12 was tested in rats with two experiments each: BT 601 and BT 601 bis (CFC-12). Experiment BT 601 bis included 60 animals (30 males and 30 females). Experiment BT 601 was started concurrently in rats of the same litters. Experiment BT 601 bis was started concurrently in rats of the same litters after experiment BT 601. At the start of the project, the animals of experiments BT 601 bis were scheduled for interim sacrifice for clinical laboratory analyses and histopathology. Since it was then decided not to perform such exams, all the animals of the experiments were treated and examined in the same way, and therefore are considered as a whole. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The concentrations in air were checked by continuous gas chromatographic monitoring-no further details referenced within the publication.
- Duration of treatment / exposure:
- The animals were exposed by inhalation, 4 hours daily, for 104 weeks (rats: Exp. BT 601, 601 bis)
- Frequency of treatment:
- 5 days weekly
- Dose / conc.:
- 0 ppm (nominal)
- Dose / conc.:
- 1 000 ppm (nominal)
- Remarks:
- (eq. to 4945 mg/m3)
- Dose / conc.:
- 5 000 ppm (nominal)
- Remarks:
- (eq. to 24726 mg/m3)
- No. of animals per sex per dose:
- 660 total (330 male & 330 female rats): 90/sex/treatment group, and 150/sex/control group
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- Detailed in table form, attached under any other information.
- Positive control:
- Not specified
- Observations and examinations performed and frequency:
- The status and behaviour of the animals were controlled three times daily.
The animals were submitted to clinical examination for gross changes every 2 weeks.
The animals were weighed every 2 weeks during treatment, and then every 8 weeks. - Sacrifice and pathology:
- Systematic and standardized histopathologic examinations were performed on each animal on the subcutaneous lymph nodes, brain and cerebellum, Zymbal glands, interscapular brown fat, salivary glands, Harderian glands, tongue, thymus and mediastinal lymph nodes, lungs, diaphragm, liver, kidneys, adrenals, spleen, mesenteric lymph nodes, stomach, various segments of the intestine, bladder, uterus, gonads, bone marrow smear, and any other organs with pathologic lesions.
Full necropsy was performed on all the animals. - Other examinations:
- Not specified
- Statistics:
- log rank test
- Clinical signs:
- no effects observed
- Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- Rats: There was no significant differences in survival linked to exposure to the test substance.
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- Rats: There was no significant differences in body weight linked to exposure to the test substance.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Clinical biochemistry findings:
- no effects observed
- Organ weight findings including organ / body weight ratios:
- not examined
- Description (incidence and severity):
- Not reported in the publication.
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- The tumors most frequently expected in the rats of the strain used, on the basis of the literature and of the historical controls of the BT Experimental Unit, are mammary tumors (benign and malignant), leukemias, pheochromocytomas and pheochromoblastomas. Moreover, a variety of other miscellaneous tumors are also observed.
FC12: Rats (Exp. BT 601 + 601 bis):
Carcinogenicity; No noticeable differences, related to treatment, were found in the incidence of total benign and malignant, and malignant tumors, and of the most frequent expected or rare tumors. - Relevance of carcinogenic effects / potential:
- No statistically significant increases in total number of tumors between treated and control groups. No carcinogenic effects were noted within the study.
- Key result
- Dose descriptor:
- NOAEC
- Effect level:
- >= 5 000 ppm (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Critical effects observed:
- no
- Conclusions:
- Under the experimental conditions, the test compound did not show carcinogenic effects.
- Executive summary:
The propellant chlorofluorocarbon dichlorodifluoromethane (CFC-12) was administered for 104 weeks to rats by inhalation at a concentration of 5000, 1000 and 0 ppm, 4 hours daily, 5days weekly.
The animals were kept under observation until spontaneous death.
No unexpected treatment-related tumors were observed in rats exposed to CFC-12. No important differences in the incidence of total benign and malignant tumors and of frequently occurring spontaneous tumors were observed in the rats exposed to CFC-12.
Under the experimental conditions, and on the basis of statistical analysis and of the oncological evaluation of the results, CFC-12 failed to show carcinogenic effects.
- Endpoint:
- carcinogenicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 1975 to 1979
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- Taken from publically available data. The study is well documented and contains suitable information for use in the assessment. The full literature report is appended for reference.
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- CFC-12 was tested by inhalation on Sprague-Dawley rats and Swiss Mice using whole body exposure. The animals were exposed by inhalation, 4 hours daily, 5 days weekly, for 104 weeks (rats: Exp. BT 601, 601 bis) and 78 weeks (mice: Exp. BT 602).
All the animals were kept under control until spontaneous death. The status and behaviour of the animals were controlled three times daily. The animals were submitted to clinical examination for gross changes every 2 weeks. The animals were weighed every 2 weeks during treatment, and then every 8 weeks. Full necropsy was performed on all the animals. The housing and the diet of the animals were the same highly standardized ones adopted in the BT Experimental Unit during the last 15 years before the beginning of this experiment. - GLP compliance:
- not specified
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source of test material: Montedison, Italy
- Purity : 99.98%
- Species:
- mouse
- Strain:
- Swiss
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Male and female Swiss mice 8 weeks old at the start of the experiment (Exp. BT 602).
The animals were of the breed currently used in the BT Experimental Unit for more than 15 years.
All the animals were kept under control until spontaneous death.
The status and behaviour of the animals were controlled three times daily.
The housing and the diet of the animals were the same highly standardized ones adopted in the BT Experimental Unit during the last 15 years before the beginning of this experiment. - Route of administration:
- inhalation
- Type of inhalation exposure (if applicable):
- whole body
- Vehicle:
- air
- Details on exposure:
- The chambers for inhalation exposure were made of stainless steel, with two glass doors, and they measure 135 x 98 x 65 cm. The volume of each chamber is 860 litres. Continuous air flow provided 12-15 air changes per hour. Before its introduction the air was filtered, and the chamber arrangement was such that air flowed from one part of the chamber to the other without recirculation. The internal pressure was about 1 mm Hg less than that of the room where the chambers were situated to avoid any possible contamination of the outside environment.
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The concentrations in air were checked by continuous gas chromatographic monitoring-no further details referenced within the publication.
- Duration of treatment / exposure:
- The animals were exposed by inhalation, 4 hours daily, for 78 weeks (mice: Exp. BT 602).
- Frequency of treatment:
- 5 days weekly
- Dose / conc.:
- 0 ppm (nominal)
- Dose / conc.:
- 1 000 ppm (nominal)
- Remarks:
- (eq. to 4945 mg/m3)
- Dose / conc.:
- 5 000 ppm (nominal)
- Remarks:
- (eq. to 24726 mg/m3)
- No. of animals per sex per dose:
- Mouse: 420 total (210 male & 210 female): 60/sex/treatment group and 90/sex/control group
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- Detailed in table form, attached under any other information.
- Positive control:
- Not specified
- Observations and examinations performed and frequency:
- The status and behaviour of the animals were controlled three times daily.
The animals were submitted to clinical examination for gross changes every 2 weeks.
The animals were weighed every 2 weeks during treatment, and then every 8 weeks. - Sacrifice and pathology:
- Systematic and standardized histopathologic examinations were performed on each animal on the subcutaneous lymph nodes, brain and cerebellum, Zymbal glands, interscapular brown fat, salivary glands, Harderian glands, tongue, thymus and mediastinal lymph nodes, lungs, diaphragm, liver, kidneys, adrenals, spleen, mesenteric lymph nodes, stomach, various segments of the intestine, bladder, uterus, gonads, bone marrow smear, and any other organs with pathologic lesions.
Full necropsy was performed on all the animals. - Other examinations:
- Not specified
- Statistics:
- log rank test
- Clinical signs:
- no effects observed
- Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- The survival rate varied from group to group, was generally lower in control than in treated groups, and showed statistically significant differences after various periods.
- Body weight and weight changes:
- no effects observed
- Description (incidence and severity):
- Mice: no effect on body weight was observed.
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- no effects observed
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- not specified
- Description (incidence and severity):
- Not reported in the publication.
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- A higher number of the following tumors was observed in treated groups:
- total number of tumors in males and females, dose-related in males;
- pulmonary adenomas in males and females, at 5000 ppm; and leukemias in males, at 5000 and 1000 ppm, and in females at 1000 ppm.
Since the above-mentioned tumors were generally age-related, a statistical method was used, namely the log rank test, which allows for such variations. When such a test was used, no statistically significant increases in total number of tumors, pulmonary adenomas, and leukemias was found in treated male or female mice in comparison with control animals. - Relevance of carcinogenic effects / potential:
- no statistically significant increases in total number of tumors between treated and control groups. No carcinogenic effects were noted within the study.
- Key result
- Dose descriptor:
- NOEC
- Effect level:
- >= 5 000 ppm (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Critical effects observed:
- no
- Conclusions:
- Under the experimental conditions, the compound failed to show any carcinogenic effects.
- Executive summary:
The propellant chlorofluorocarbon dichlorodifluoromethane (CFC-12) was administered by inhalation for 78 weeks to mice at a concentration of 5000, 1000 and 0 ppm, 4 hours daily, 5 days weekly.
The animals were kept under observation until spontaneous death.
The incidence of all tumors and of some particular frequently occurring spontaneous tumors in mice showed a tendency to increase in animals exposed to CFC-12. The increased incidence was usually observed in one sex and was not always dose-related, possibly due to a longer survival of the treated mice compared with controls.
Under the experimental conditions, and on the basis of statistical analysis and of the oncological evaluation of the results, CFC-12 failed to show carcinogenic effects.
Referenceopen allclose all
Dichlorodifluoromethane (FC12): Total Tumors in Rats (Exp. BT 601 + 601 bis)
Group No. |
Concentration (ppm) |
Animals |
Percentage of Animals Bearing Tumors |
No. of Malignant Tumors per 100 Animals |
||
Sex |
No. at Start |
TBMTa |
MTb |
|||
I |
5000 |
M |
90 |
30.0 |
10.0 |
10.0 |
F |
90 |
80.0 |
20.0 |
20.0 |
||
M + F |
180 |
55.0 |
15.0 |
15.0 |
||
II |
1000 |
M |
90 |
46.7 |
17.8 |
17.8 |
F |
90 |
78.9 |
26.7 |
26.7 |
||
M + F |
180 |
62.8 |
22.2 |
22.2 |
||
III |
0 (Control) |
M |
150 |
34.0 |
16.7 |
17.3 |
F |
150 |
82.7 |
28.7 |
31.3 |
||
M + F |
300 |
58.3 |
22.7 |
24.3 |
aTotal benign and malignant tumors.
bMalignant tumors.
Dichlorodifluoromethane (FC12): Mammary Tumors, Leukemias, Pheochromocytomas and Pheochromoblastomas in Rats (Exp. BT 601 + 601 bis)
Group No. |
Concentration (ppm) |
Animals |
Percentage of Animals Bearing Tumors |
|||||
Sex |
No. at Start |
Mammary Tumors |
|
|||||
BMTa |
MTb |
Leukemiasc |
Pheochromocytomas |
Pheochromoblastomas |
||||
I |
5000 |
M |
90 |
12.2 |
2.2 |
3.3 |
5.5 |
- |
F |
90 |
74.4 |
10.0 |
1.1 |
1.1 |
- |
||
M + F |
180 |
43.3 |
6.1 |
2.2 |
3.3 |
- |
||
II |
1000 |
M |
90 |
15.5 |
1.1 |
7.8 |
12.2 |
1.1 |
F |
90 |
68.9 |
14.4 |
3.3 |
1.1 |
- |
||
M + F |
180 |
42.2 |
7.8 |
5.5 |
6.7 |
0.5 |
||
III |
0 (Control) |
M |
150 |
12.7 |
4.0 |
6.0 |
4.0 |
- |
F |
150 |
72.0 |
13.3 |
5.3 |
3.3 |
- |
||
M + F |
300 |
42.3 |
8.7 |
5.7 |
3.7 |
- |
aBenign and malignant tumors.
bMalignant tumors.
cThe term “leukemia” includes a variety of hemolymphoreticular neoplastic diseases at different sites.
Dichlorodifluoromethane (FC12): Liver Angiosarcomas in Rats
Experiment and Compound |
Group No. |
Concentration (ppm) |
Animals |
Percentage of Animals Bearing Liver Angiosarcomas |
|
Sex |
No. at Start |
||||
BT 601 + BT 601 bis (FC12) |
I |
5000 |
M |
90 |
- |
F |
90 |
3.3 |
|||
M + F |
180 |
1.7 |
|||
II |
1000 |
M |
90 |
- |
|
F |
90 |
1.1 |
|||
M + F |
180 |
0.5 |
|||
III |
0 (Control) |
M |
150 |
0.7 |
|
F |
150 |
0.7 |
|||
M + F |
300 |
0.7 |
Dichlorodifluoromethane (FC12): Total Tumors in Mice (Exp. BT 602)
Group No. |
Concentration (ppm) |
Animals |
Percentage of Animals Bearing Tumors |
No. of Malignant Tumors per 100 Animals |
||
Sex |
No. at Start |
TBMTa |
MTb |
|||
I |
5000 |
M |
60 |
25.0 |
11.7 |
11.7 |
F |
60 |
21.7 |
10.0 |
10.0 |
||
M + F |
120 |
23.3 |
10.8 |
10.8 |
||
II |
1000 |
M |
60 |
15.0 |
6.7 |
6.7 |
F |
60 |
25.0 |
23.3 |
23.3 |
||
M + F |
120 |
20.0 |
15.0 |
15.0 |
||
III |
0 (Control) |
M |
90 |
10.0 |
5.5 |
5.5 |
F |
90 |
16.7 |
10.0 |
11.1 |
||
M + F |
180 |
13.3 |
7.8 |
8.3 |
aTotal benign and malignant tumors.
bMalignant tumors.
Dichlorodifluoromethane (FC12): Mammary Carcinomas, Pulmonary Tumors and Leukemias in Mice (Exp. BT 602)
Group No. |
Concentration (ppm) |
Animals |
Percentage of Animals Bearing Tumors |
||||
Sex |
No. at Start |
Mammary Carcinomas |
Pulmonary Tumors |
Leukemiasa |
|||
Adenomas |
Adenocarcinomas |
||||||
I |
5000 |
M |
60 |
- |
8.3 |
- |
6.7 |
|
|
F |
60 |
- |
5.0 |
- |
10.0 |
|
|
M + F |
120 |
- |
6.7 |
- |
8.3 |
II |
1000 |
M |
60 |
- |
5.0 |
- |
6.7 |
|
|
F |
60 |
3.3 |
1.7 |
- |
20.0 |
|
|
M + F |
120 |
1.7 |
3.3 |
. |
13.3 |
III |
0 (Control) |
M |
90 |
- |
3.3 |
- |
3.3 |
|
|
F |
90 |
1.1 |
2.2 |
- |
8.9 |
|
|
M + F |
180 |
0.5 |
2.8 |
- |
6.1 |
aThe term “leukemia” includes a variety of hemolymphoreticular beoplastic diseases at different sites.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Quality of whole database:
- Study is considered to be appropriate for use as it presents well documented results in an appropriate format, despite not being to GLP.
Calculation based on 5000 ppm * 120.91 /24.45 = 24725 mg/m3 where 24.45 is the molar volume as reported into the ACGIH ("2010 TLVs and BEIs, Based on the Documentation of the Threshold LImit Values for Chemical Substances and Physical Agents & Biological Exposure Indices") for conversion ppm vs mg/m3.
Carcinogenicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
The inhalation studies were not conducted to GLP and is not in compliance with current protocols. However these results are considered appropriate for use in a weight of evidence. In addition, results of a chronic oral study were also available.
No adverse effects were reported following the 2-year exposure by inhalation or by oral exposure to the substance.
The above results triggered no classification under the CLP Regulation (EC No 1272/2008). No classification for carcinogenic effects is therefore required.
Additional information
A carcinogenicity study on the substance was conducted. Dichlorodifluoromethane (CFC-12) was administered by inhalation at a concentration of 5000, 1000 and 0 ppm, 4 hours daily, 5 days weekly, for 104 and 78 weeks, to rats and mice, respectively.
As a result of this study, no unexpected treatment-related tumors were observed in rats exposed. No important differences in the incidence of total benign and malignant tumors and of frequently occurring spontaneous tumors were observed in the rats exposed to the tested propellant. The incidence of all tumors and of some particular frequently occurring spontaneous tumors in mice showed a tendency to increase in animals exposed to CFC-12. The increased incidence was usually observed in one sex and was not always dose-related, possibly due to a longer survival of the treated mice compared with controls.
Under the experimental conditions, despite study limitations and lack fo details in available sources, CFC-12 failed to show carcinogenic effects in rats and mice.
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.