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Home » Study Results & Research Projects » NTP Study Reports » All Long-Term Reports » Abstract for TR-450 - Tetrafluoroethylene
Chemical Formula: C 2F 4 | - | 3D Structure* |
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Tetrafluoroethylene is used in the production of polytetrafluoroethylene (Teflon®) and other polymers. Tetrafluoroethylene was nominated by the National Cancer Institute for toxicity and carcinogenicity studies based on the potential for human exposure to the chemical due to the large production volume and on the lack of adequate data for tetrafluoroethylene in the literature. Male and female F344/N rats and B6C3F1 mice were exposed to tetrafluoroethylene (98% to 99% pure) by whole body inhalation exposure for 16 days, 13 weeks, or 2 years. Genetic toxicity studies were conducted in mouse peripheral blood erythrocytes.
Groups of five male and five female F344/N rats were exposed to 0, 312, 625, 1,250, 2,500, or 5,000 ppm tetrafluoroethylene by inhalation for 6 hours per day, 5 days per week for a total of 12 exposures during a 16-day period. All rats survived to the end of the study. The final mean body weights and body weight gains of males and females exposed to 5,000 ppm were significantly less than those of the controls. The mean body weight gain of females exposed to 2,500 ppm was also significantly less than that of the controls. There were no exposure-related clinical findings in male or female rats. There were no significant differences in hematology parameters that were considered to be related to tetrafluoroethylene exposure. Absolute and relative kidney weights of all exposed groups of males were significantly greater than those of the controls, as were those of females in the 2,500 and 5,000 ppm groups. The absolute kidney weight of females exposed to 1,250 ppm was also significantly greater than that of the controls. The relative liver weights of all exposed groups of males and the absolute liver weights of males in the 625 and 2,500 ppm groups were significantly greater than those of the controls. Increased incidences of renal tubule degeneration occurred in males and females exposed to 625 ppm or greater; this lesion was located predominantly at the corticomedullary junction. The severity of degeneration increased with increasing exposure concentration and was slightly greater in males than females.
Groups of five male and five female B6C3F1 mice were exposed to 0, 312, 625, 1,250, 2,500, or 5,000 ppm tetrafluoroethylene by inhalation for 6 hours per day, 5 days per week for a total of 12 exposures during a 16-day period. All mice survived to the end of the study. Final mean body weights and body weight gains of all exposed groups of mice were similar to those of the controls. There were no exposure-related clinical findings in male or female mice. There were no significant differences in hematology parameters that were considered to be related to tetrafluoroethylene exposure. The absolute and relative liver weights of females exposed to 5,000 ppm were significantly greater than those of the controls, as was the absolute kidney weight of females in that group and the absolute liver weight of females in the 2,500 ppm group. Renal tubule karyomegaly was observed in male and female mice in the 1,250, 2,500, and 5,000 ppm groups, and the severity of this lesion increased with increasing exposure concentration. Karyomegaly was located predominantly in the inner renal cortex.
Groups of 10 male and 9 or 10 female F344/N rats were exposed to 0, 312, 625, 1,250, 2,500, or 5,000 ppm tetrafluoroethylene by inhalation for 6 hours per day, 5 days per week, for 13 weeks. All rats survived to the end of the study. The final mean body weight and body weight gain of males exposed to 5,000 ppm were significantly less than those of the controls, as was the mean body weight gain of females in this exposure group. There were no clinical findings attributed to exposure to tetrafluoroethylene. Exposure of rats to tetrafluoroethylene resulted in a concentration-dependent normocytic, normochromic, nonresponsive anemia consistent with a secondary hypoproliferative anemia. An exposure concentration-dependent proteinuria also occurred, consistent with renal tubule degeneration observed histopathologically. The absolute and relative liver weights of all exposed groups of males and of females in the 5,000 ppm group were significantly greater than those of the controls. The absolute and relative right kidney weights of males and females exposed to 1,250 ppm or greater and of females in the 625 ppm group were also significantly greater than those of the controls. There were no differences in sperm morphology or vaginal cytology parameters between control and exposed groups of rats. Incidences of renal tubule degeneration in males exposed to 625 ppm or greater and in females exposed to 2,500 or 5,000 ppm were significantly greater than those in the controls. Renal lesions were similar to those observed in the 16-day study and were located predominantly at the corticomedullary junction.
Groups of 10 male and 10 female B6C3F1 mice were exposed to 0, 312, 625, 1,250, 2,500, or 5,000 ppm tetrafluoroethylene by inhalation for 6 hours per day, 5 days per week, for 13 weeks. All mice survived to the end of the study. Final mean body weights and body weight gains of all exposed groups of male and female mice were generally similar to those of the controls. There were no clinical findings that were considered to be related to tetrafluoroethylene exposure. Exposure of mice to tetrafluoroethylene resulted in a concentration-dependent normocytic, normochromic, nonresponsive anemia, consistent with a secondary hypoproliferative anemia, and in polyuria. Differences in sperm morphology parameters and estrous cycle lengths were not considered to be exposure related. Incidences of karyomegaly of the renal tubule epithelial cells in male and female mice exposed to 1,250 ppm or greater were significantly greater than those in the controls. Karyomegaly was similar to that observed in the 16-day study and was observed primarily in the inner renal cortex.
Groups of 60 male rats were exposed to 156, 312, or 625 ppm and groups of 60 female rats were exposed to 312, 625, or 1,250 ppm tetrafluoroethylene by inhalation for 6 hours per day, 5 days per week, for 104 weeks, with an observation period of 11 days following the final exposure. Ten male and ten female rats from each exposure group were evaluated at 15 months for organ weights and clinical pathology.
Survival, Body Weights, and Clinical Findings
Survival rates of males in the 625 ppm group and of all exposed
groups of females were significantly less than those of the controls.
Mean body weights of males exposed to 625 ppm were lower than
those of the controls from week 81 until the end of the study,
and the mean body weight of 1,250 ppm females was slightly lower
than that of the controls at the end of the study. The only clinical
finding associated with exposure to tetrafluoroethylene was opacity
of the eyes in exposed groups of female rats; this change was
observed microscopically as cataracts.
Hematology, Clinical Chemistry, and Urinalysis
At the 15-month interim evaluation, there were no differences
in hematology, clinical chemistry, or urinalysis parameters that
were considered to be related to tetrafluoroethylene exposure.
Pathology Findings
The absolute and relative kidney weights of males exposed to 625
ppm and females exposed to 1,250 ppm and the absolute kidney weight
of females exposed to 625 ppm were significantly greater than
those of the controls at the 15-month interim evaluation. At 15
months, renal tubule hyperplasia was observed in one male exposed
to 312 ppm and one male and one female exposed to 625 ppm; oncocytic
hyperplasia was observed in one female exposed to 1,250 ppm. At
the end of the study, incidences of renal tubule adenoma were
greater in males and females exposed to 312 ppm or greater than
those in the controls. This exposure-related increase was confirmed
by examination of step sections (extended evaluations). At the
end of the study, the incidences of renal tubule hyperplasia in
males exposed to 625 ppm and females exposed to 1,250 ppm were
significantly greater than those in the controls. The incidences
of renal tubule adenoma and renal tubule adenoma or carcinoma
(combined) in the extended evaluations and in the standard and
extended evaluations (combined) in the 1,250 ppm female group
and the 625 ppm male group were significantly greater than those
in the controls, and the incidences occurred with significant
positive trends. Oncocytic hyperplasia was observed at the end
of the study in one male exposed to 312 ppm and in three females
exposed to 1,250 ppm. At 15 months and at the end of the study,
the incidences of renal tubule degeneration in all exposed groups
of males and in females in the 625 and 1,250 ppm groups were greater
than those in the controls. Renal tubule degeneration was similar
to that observed in the 13-week study and was located predominantly
at the corticomedullary junction. The severity of nephropathy
generally increased with increasing exposure concentration in
male rats at 15 months and 2 years.
The absolute and relative liver weights of females in the 1,250 ppm group and the absolute liver weight of females exposed to 625 ppm were significantly greater than those of the controls at the 15-month interim evaluation. At 2 years, the incidences of hepatocellular carcinoma and hepatocellular adenoma or carcinoma (combined) in males exposed to 312 ppm, the incidences of hepatocellular adenoma and adenoma or carcinoma (combined) in females in all exposed groups, and the incidences of hepatocellular carcinoma in females exposed to 312 or 625 ppm were significantly greater than those in the controls. Also at 2 years, the incidence of hemangiosarcoma in females exposed to 625 ppm was significantly greater than that in the controls. In all exposed groups of males, the incidences of clear cell foci at 15 months were greater than those in the controls; at 2 years, the incidences of eosinophilic foci in all exposed groups of males and the incidences of basophilic and mixed cell foci in males in the 312 and 625 ppm groups were greater than those in the controls. The incidences of mixed cell foci at 15 months in females exposed to 625 or 1,250 ppm and at 2 years in females exposed to 1,250 ppm were also significantly greater than those in the controls. At the end of the 2-year study, increased incidences of cystic degeneration occurred in the liver of all exposed groups of males, and increased incidences of hepatic angiectasis were observed in exposed groups of females.
Incidences of mononuclear cell leukemia in males exposed to 156 ppm and in all exposed groups of females were significantly greater than those in the controls.
Incidences of cataracts in females exposed to 1,250 ppm were greater than those in the controls at the end of the 2-year study.
At the end of the study, there were slight increases in the incidences of testicular interstitial cell adenoma in rats exposed to 312 or 625 ppm.
Groups of 58 male and 58 female B6C3F1 mice were exposed to 0, 312, 625, or 1,250 ppm tetrafluoroethylene by inhalation for 6 hours per day, 5 days per week, for 95 to 96 weeks. Ten male and ten female mice from each exposure group were evaluated at 15 months for organ weights.
Survival, Body Weights, and Clinical Findings
The survival rates of all exposed groups of males and females
were significantly less than those of the controls. Because of
the reduced survival due to exposure-related liver neoplasms,
the study was terminated during week 96. Mean body weights of
exposed groups of males and females were generally similar to
those of the controls, except at the end of the study, when they
were somewhat less than those of the controls. There were no clinical
findings related to tetrafluoroethylene exposure.
Pathology Findings
At the 15-month interim evaluation, there were no differences
in absolute or relative kidney, liver, or lung weights between
exposed and control groups of mice. At the end of the study, the
incidences of multifocal coagulative necrosis of the liver were
increased in males in the 625 and 1,250 ppm groups. Also at the
end of the study, females in all exposed groups had greater incidences
of hematopoietic cell proliferation in the liver than the controls.
Angiectasis occurred in all exposed groups of males and females
at 15 months and at the end of the study. At the 15-month interim
evaluation, hemangiosarcomas were observed in three males exposed
to 1,250 ppm and in one female exposed to 312 ppm. The incidences
of hemangiosarcoma in all exposed groups of males and females
at the end of the study were significantly greater than those
in the controls and exceeded the historical chamber control ranges.
Also at the end of the study, the incidences of hemangioma in
males and females exposed to 312 ppm and in males exposed to 625
ppm were also significantly greater than those in the controls
and exceeded the range in historical chamber controls. At 15 months,
hepatocellular adenomas and carcinomas occurred in control males
and all exposed groups of males and females. Females exposed to
625 or 1,250 ppm had significantly greater incidences of eosinophilic
foci than the controls at the 15-month interim evaluation. At
the end of the study, the incidences of eosinophilic foci in males
exposed to 625 or 1,250 ppm and in females exposed to 312 or 625
ppm were significantly greater than those in the controls. In
male and female mice, increased incidences of a variety of hepatocellular
neoplasms, including adenomas, multiple adenomas, carcinomas,
and multiple carcinomas, were considered related to tetrafluoroethylene
exposure.
At the end of the study, the incidences of histiocytic sarcoma (all organs) in all exposed groups of males and females were significantly greater than those in the controls and exceeded the historical control ranges for all organs. The greatest incidences of histiocytic sarcomas were observed in the liver and lung, but these neoplasms were also observed in the spleen, lymph nodes, bone marrow, and kidney.
Significantly increased incidences of renal tubule dilatation (males) and karyomegaly (males and females), located predominantly in the inner cortex, were observed in mice exposed to 625 or 1,250 ppm at 15 months. At the end of the study, the increased incidences of dilatation and karyomegaly in all exposed groups of males and of karyomegaly in 1,250 ppm females were generally significant.
Incidences of hematopoietic cell proliferation in the spleen of all exposed groups of males and females were significantly greater than those in the controls at the end of the study. Additionally, the severity of this lesion increased with increasing exposure concentration.
No increases in the frequency of micronucleated erythrocytes were observed in peripheral blood samples obtained from male and female mice at the end of the 13-week inhalation study of tetrafluoroethylene.
Under the conditions of these 2-year inhalation studies, there was clear evidence of carcinogenic activity of tetrafluoroethylene in male F344/N rats based on increased incidences of renal tubule neoplasms (mainly adenomas) and hepatocellular neoplasms. There was clear evidence of carcinogenic activity of tetrafluoroethylene in female F344/N rats based on increased incidences of renal tubule neoplasms, liver hemangiosarcomas, hepatocellular neoplasms, and mononuclear cell leukemia. There was clear evidence of carcinogenic activity of tetrafluoroethylene in male and female B6C3F1 mice based on increased incidences of liver hemangiomas and hemangiosarcomas, hepatocellular neoplasms, and histiocytic sarcomas.
Slight increases in the incidences of mononuclear cell leukemia and testicular interstitial cell adenomas in male rats may have been related to exposure to tetrafluoroethylene.
Exposure of rats to tetrafluoroethylene resulted in increased incidences of renal tubule hyperplasia and degeneration in males and females, increased severity of kidney nephropathy in males, and increased incidences of liver angiectasis and cataracts in females. Exposure of mice to tetrafluoroethylene resulted in increased incidences of hematopoietic cell proliferation of the liver in females, liver angiectasis in males and females, renal tubule dilatation in males, renal tubule karyomegaly in males and females, and splenic hematopoietic cell proliferation in males and females.
Synonyms: Perfluoroethylene; tetrafluoroethene; 1,1,2,2-tetrafluoroethylene; TFE
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Male
F344/N Rats |
Female
F344/N Rats |
Male
B6C3F1 Mice |
Female
B6C3F1 Mice | ||
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Exposure
Concentrations |
0, 156, 312, or 625 ppm | 0, 312, 625, or 1,250 ppm | 0, 312, 625, or 1,250 ppm | 0, 312, 625, or 1,250 ppm | |
Body Weights | 625 ppm group lower than controls | 1,250 ppm group slightly lower than controls at end of study | Exposed groups lower than controls at end of study | Exposed groups lower than controls at end of study | |
Survival Rates | 17/50, 12/50, 17/50, 1/50 (2 years) | 28/50, 16/50, 15/50, 18/50 (2 years) | 38/48, 11/48, 2/48, 1/48 (22 months) | 36/48, 4/48, 6/48, 4/48 (22 months) | |
Nonneoplastic
Effects |
Kidney (renal tubule): hyperplasia (single sections - 1/50, 1/50, 1/50, 6/50; single and step sections - 7/50, 11/50, 7/50, 24/50); degeneration (2/50, 20/50, 50/50, 49/50);severity of nephropathy (2.3, 1.9, 2.7, 3.5) | Kidney (renal tubule): hyperplasia (single sections - 1/50, 3/50, 6/50, 12/50; single and step sections - 3/50, 6/50, 11/50, 25/50); degeneration (0/50, 0/50, 35/50, 46/50),
Liver: angiectasis (0/50, 9/50, 9/50, 14/50) Eye: cataracts (15/50, 4/50, 10/50, 45/50) |
Liver : angiectasis (0/48, 6/48, 10/48, 13/48)
Kidney (renal tubule): dilatation (0/48, 4/48, 16/48, 36/48); karyomegaly (1/48, 2/48, 10/48, 28/48) Spleen:hematop oietic cell proliferation (14/48, 32/48, 41/46, 42/46) |
Liver : hematop oietic cell proliferation (3/48, 19/48, 13/47, 15/47); angiectasis (1/48, 9/48, 6/47, 4/47)
Kidney (renal tubule): karyomegaly (0/48, 0/48, 0/47, 38/48) Spleen: hematop oietic cell proliferation (18/48, 39/48, 41/46, 41/47) | |
Neoplastic Effects | Kidney (renal tubule): adenoma (single sections - 0/50, 0/50, 6/50, 3/50; single and step sections - 2/50, 4/50, 9/50, 13/50); carcinoma (single sections - 1/50, 0/50, 2/50, 0/50; single and step sections - 1/50, 1/50, 2/50, 0/50); adenoma or carcinoma (single sections - 1/50, 0/50, 6/50, 3/50; single and step sections - 3/50, 5/50, 9/50, 13/50)
Liver: hepatocellular carcinoma (1/50, 1/50, 10/50, 3/50); hepatocellular adenoma or carcinoma (4/50, 7/50, 15/50, 8/50) |
Kidney (renal tubule): adenoma (single sections - 0/50, 3/50, 1/50, 3/50; single and step sections - 0/50, 3/50, 3/50, 8/50); carcinoma (single sections - 0/50, 0/50, 0/50, 2/50; single and step sections - 0/50, 0/50, 0/50, 3/50); adenoma or carcinoma (single sections - 0/50, 3/50, 1/50, 5/50; single and step sections - 0/50, 3/50, 3/50, 10/50)
Liver: hemangiosarcoma (0/50, 0/50, 5/50, 1/50); hepatocellular adenoma (0/50, 4/50, 5/50, 6/50); hepatocellular carcinoma (0/50, 4/50, 9/50, 2/50); hepatocellular adenoma or carcinoma (0/50, 7/50, 12/50, 8/50) Mononuclear cell leukemia : (16/50, 31/50, 23/50, 36/50) |
Liver : hemangioma (0/48, 10/48, 5/48, 2/48); hemangiosarcoma (0/48, 21/48, 27/48, 37/48); hemangioma or hemangiosarcoma (0/48, 26/48, 30/48, 38/48); hepatocellular carcinoma (11/48, 20/48, 33/48, 26/48); hepatocellular adenoma or carcinoma (26/48, 34/48, 39/48, 35/48)Hematopoietic system (all organs): histiocytic sarcoma (0/48, 12/48, 7/48, 7/48) | Liver: hemangioma (0/48, 5/48, 2/47, 1/47); hemangiosarcoma (0/48, 27/48, 27/47, 34/47); hemangioma or hemangiosarcoma (0/48, 31/48, 28/47, 35/47); hepatocellular carcinoma (4/48, 28/48, 22/47, 20/47); hepatocellular adenoma or carcinoma (17/48, 33/48, 29/47, 28/47)
Hematopoietic system (all organs: histiocytic sarcoma (1/48, 21/48, 19/47, 18/48) | |
Uncertain
Findings |
Mononuclear cell leukemia : (34/50, 43/50, 38/50, 31/50) Testis: interstitial cell adenoma (39/50, 40/50, 48/50, 47/50) | None | None | None | |
Level of Evidence
of Carcinogenic Activity |
Clear evidence | Clear evidence | Clear evidence | Clear evidence | |
Genetic Toxicology |
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Micronucleated erythrocytes Mouse peripheral blood in vivo : Negative |
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Report Date: April 1997
Pathology Tables, Survival and Growth Curves from NTP 2-year Studies
Target Organs & Incidences from 2-year Studies
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