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lung cancer research, lung cancer studies, lung research, lung studies, lung tumor research, lung tumor studies
lung cancer research, lung cancer studies, lung research, lung studies, lung tumor research, lung tumor studies

Human Studies of PCBs and Lung Cancer 

lung cancer research, lung cancer studies, lung research, lung studies, lung tumor research, lung tumor studies

This may not be a complete list of all lung cancer research involving PCB exposures.  For more lung cancer studies, visit the TOXNET database operated by the National Library of Medicine (the source of these abstracts.) Keep in mind that these studies are not all equal in size or quality. Some were published in peer-reviewed journals, while others were simply presented at conferences. A few are duplicates by the same author (one conference-based, another published) but we presented both because the descriptions were slightly different.

lung cancer research, lung cancer studies, lung research, lung studies, lung tumor research, lung tumor studies

Study #1

  • PCBs were linked to a statistically significant increase in lung cancer deaths
A PCB-exposed group in Japan had a statistically significant increase in lung cancer deaths. This was a case involving rice oil contaminated with PCBs and furans. [Some scientists argue that the cancers were due to the furans, not the PCBs; however, commercial mixtures of PCBs generally came contaminated with furans from the manufacturer. The Fox River is contaminated with both PCBs and furans as a result, and both chemicals are picked up and accumulated in fish.] (Kuratsune et al, 1987)

Study #2

  • PCBs were linked to an increase in lung cancer deaths
This study followed employees who had worked at Monsanto's PCB production plant. The researchers found that the incidence of lung cancer deaths among these workers was somewhat higher than would ordinarily be expected. The increase, however, was not considered statistically significant. (Zack et al, 1979)

Study #3

  • PCBs may be associated with an increased incidence for all cancers combined, including lung cancer, in 5,088 men studied
Calculated cumulative exposures to electromagnetic (EM) fields during the production and distribution of hydroelectric power and the incidence of cancer were compared. The study cohort included 5,088 men employed in eight large Norwegian hydroelectric power companies. They had been employed for at least 1 year between 1920 and 1985. During the follow up period from 1951 through 1991, 486 new cases of cancer were observed. Stomach cancer showed an excess risk among workers with more than 30 years on the job. An increase in the standardized incidence ratio was detected for malignant melanoma as well. An analysis by duration of employment indicated an increased incidence ratio for all cancers combined, cancer of the pancreas, lung, and kidney, malignant melanoma, nonmelanoma, and lymphoma. Of the three cases of leukemia, two were among workers who had been employed for less than 20 years. An excess risk was noted for malignant melanoma at cumulative exposures above 35 microtesla years. The evaluation of risk for malignant melanoma and combined exposures to magnetic fields and possible exposure to electric discharges or to oils contaminated with polychlorinated biphenyls showed a tendency toward an effect. The authors conclude that no association was observed between the occurrence of leukemia or brain tumors and exposure to electric or magnetic fields in hydroelectric power companies. (Tynes et al, 1994)

Study #4

  • lung cancer deaths were elevated, but not considered statistically significant
  • small number of deaths limits interpretation
  • results support the possibility of PCBs posing a carcinogenic risk to humans
A study of mortality in electrical capacitor manufacturing workers was conducted. The cohort consisted of 2100 workers, 1556 females, employed for at least 1 week at a capacitor manufacturing facility at Milan, Italy, between 1946 and 1978. The facility used polychlorinated-biphenyls (1336363) (PCBs) as the dielectric fluid until 1980. Vital status of the cohort at the end of 1982 was determined. Death certificates for all decedents were reviewed. Standardized mortality ratios (SMRs) were computed, based on national and local mortality rates. Overall mortality among male workers, 30 deaths, was similar to that expected. There were 14 deaths due to cancer, which was significantly more than expected, based on either local or national rates. Deaths due to cancer of the gastrointestinal tract were significantly elevated. Deaths due to lung cancer and hematologic neoplasms were nonsignificantly elevated. Female workers showed an overall mortality, 34 deaths, that was significantly increased above that expected. Twelve cancer deaths were observed, against 5.3 expected using the local population for comparison. Deaths due to hematologic neoplasms were significantly increased above that expected, 4 observed versus 1.1 expected based on local mortality rates. There was a significant deficit of deaths due to cardiovascular disease. Accidental deaths were significantly elevated, with a SMR of 225. The authors note that the small number of deaths limits interpretation of the results. The results, however, agree with those of previous studies and support the possibility of PCBs posing a carcinogenic risk to humans. (Bertazzi et al, 1987)

Study #5

  • 16 of 58 employees (27.6 percent) had lung cancer and were probably exposed to PCBs
In response to a request from OSHA, possible hazardous working conditions at the McGraw-Edison (SIC-3612) facility located in Canonsburg, Pennsylvania were investigated. The company produced large power transformers plus various sizes of power circuit breakers. Exposures to welding fumes, high voltage electricity, paint solvent vapors, noise, and transformer oils were possible. Past exposures to oils containing polychlorinated-biphenyls (1336363), and asbestos (1332214) were possible. A group of 58 employees was examined in an attempt to verify possible clustering of cancer cases. Of the original 58, no records were found for three, and 18 individuals had died but had never had cancer. The remaining 37 were all confirmed cancer cases covering 13 different types. An apparent clustering of cancer in recent years was demonstrated. All but one case occurred in white males between the ages of 43 and 69 years. Lung cancer was the most common type, 16 of the 37 cases. The authors conclude that, compared with the general population, lung cancer was occurring probably at no greater rate among these employees than in the general population. No evidence was found to associate causally the number of cancer cases among the workers and any occupational exposures they may have been experiencing at this facility. The authors recommend that a thorough industrial hygiene survey be made at this facility. (Sanderson et al, 1988)

Study #6

  • tumors in patients who inadvertently consumed PCBs in 1968 included lung cancer
The general toxic effects and the carcinogenic potential of the polychlorinated biphenyls (1336363) (PCBs) were reviewed. Low level exposure of primates to PCBs has caused widespread deleterious effects that persist indefinitely. General effects of the PCBs in man and in nonhuman primate experimental animals were discussed. In man, the effects have included fatigue, headaches, digestive disorders, menstrual disturbances, and hyperpigmentation in infants born to mothers exposed to PCBs. In experimental animals, the most consistent tissue modification has been a marked hypertrophy of the liver. Biochemical implications of the PCBs as possible carcinogens were discussed in terms of several metabolites and their association with cellular macromolecules. Morphological changes and tumor development associated with chronic feeding of PCBs to rodents and monkeys were described, including neoplastic liver nodules, liver adenofibrosis, hepatocellular carcinomas, and hyperplastic and metaplastic alterations of the stomach. Preliminary observations on the association of PCBs and tumor development in man were reviewed. Tumors in patients who inadvertently consumed PCBs in 1968 have included one or more occurrences of stomach, liver, lung, and breast cancers, malignant melanomas, and a malignant lymphoma. The author concludes that although there is only suggestive evidence that persons exposed to PCBs have a higher incidence of cancer, the data that have been obtained in lower animals warrant concern in man, and that until a better understanding of the potential danger of low level, long term exposure is established, it appears that any level of exposure may be injurious to human health. (Allen et al, 1977)

Study #7

  • two workers out of 19 developed lung cancer, but the study was too small to calculate significance
  • the results do not exclude the possibility of a cancer risk from PCBs
Mortality and cancer incidence of a cohort of 142 Swedish male workers engaged in the manufacturing of capacitors, who were exposed to polychlorinated-biphenyls (PCBs) for at least 6 months between 1965 and 1978, were investigated. Mean exposure time was 6.5 years. Previous sampling and analysis of airborne PCBs showed a level of 0.1mg/m3. Expected numbers, standardized for sex, age and calendar year, were calculated from national statistics. Twenty-two deaths were reported between 1965 and 1982, and seven cancers were reported between 1965 and 1980; both figures were in good agreement with those expected. Latency time ranged from 4 to 22 years (median of 13 years). The separate analysis of 19 workers with a higher exposure (capacitor fillers and repairmen) did not show increased trends of mortality or cancer incidence. Two workers had lung cancer, and one developed a slow growing mesenchymal tumor and a malignant lymphoma, both occurring after 10 years of exposure. Although the size of the cohort was small and the follow up time short, the authors conclude that the results obtained do not indicate any excess mortality or cancer incidence at the facility studied, however, they do not exclude the possibility of a carcinogenic risk from PCB exposure. (Gustavsson et al, 1986)

Study #8

  • two of 12 autopsies found lung cancer in PCB poisoning victims
Autopsy findings of 12 patients with yusho including 2 stillborn babies are reported. Characteristic pathological changes were acne-like eruptions and cutaneous pigmentation with histological features of follicular hyperkeratosis, dilated hair follicles, and an increase of melanin pigment of the epidermis. In addition to the skin lesions, multiplication of the duct epithelium of the esophageal gland was found in 6 patients. Unusual multiple small foci of myocardial necrosis and fibrosis with basophilic myofibrillar degeneration were found in one patient, suggesting a relation to PCB exposure. Five cases with carcinomas (two involving the liver, two the lung, and one the esophagus) were also found, but their causal relationship with PCB was not certain. Nine cases showed the characteristic gas chromatographic pattern of yusho, but two cases had the same one as that of healthy controls. (Kikuchi, 1984)

Study #9

  • firefighters are often exposed to PCBs
  • firefighters have a higher incidence of lung cancer
The long term health hazards of fire fighting are reviewed. Although the physical dangers of the occupations are obvious, dangers from inhaling toxic gases, some carcinogenic, in heated air and fumes are not so readily apparent. Liver and kidney problems, the incidence of birth defects among offspring, and increased susceptibility to infectious disease are all cited as problems needing investigation. Available data suggests that fire fighters have a higher incidence of cancer of the mouth and throat, lungs and lymph system, and intestines and rectum. It is suggested that due to the increased use of plastics, risks from smoke inhalation have greatly increased for fire fighters. Some of the toxic components of certain plastics whose primary function is to suppress smoke and retard flame make the smoke more toxic when these materials get hot enough to burn. Lung hazards produced by acrylonitrile (107131), asbestos (1332214), cadmium (7440439), carbon-tetrachloride (56235), chromium (7440473), creosote (8021394), benzene (71432), and polychlorinated biphenyls are considered. It is recommended that fire departments clear their facilities of deteriorating asbestos gloves, uniforms, or blankets. Legislation and regulation are also recommended to direct use of alternative materials which would be less toxic when they burn. (Polakoff, 1984)

Study #10

  • abnormal serum oncogene proteins in workers with known exposure to carcinogens (such as PCBs) may represent an early marker of neoplastic disease (cancer)
A new technique for detecting serum oncogene proteins was described and tested in municipal workers exposed to polychlorinated-biphenyls (1336363) (PCBs). The study group was selected from a group of 24 municipal employees exposed to the PCBs in transformer oil during the removal and cleaning of old transformers. A total of 16 workers submitted to a complete evaluation including a medical and occupational history, possible sources of other PCB exposures, exposures to other hazardous materials, complete physical and dermatological examination, and laboratory tests for serum triglycerides, serum PCB levels, liver function tests, and the presence of oncogene related proteins in the serum. The assay for serum oncogene proteins was based on a modification of the urine immunoblot method. The average age of the 16 workers was 42 years, and all reported some skin contact with the transformer oil during the clean up and removal operations. Two workers reported prior exposure to PCBs, and seven reported exposure to other carcinogenic materials. Twelve of the sixteen workers were current or recent cigarette smokers. Serum PCB levels were negligible in 11 of the 16 workers and ranged from 0.6 to 10.6 parts per billion in the other five workers. Eight workers showed abnormal serum oncogenes not found in normal unexposed individuals. Six workers with positive smoking histories showed abnormal oncogenes of the fes variety; fes type proteins were not observed in any nonsmokers. The ras related oncogenes were detected in three workers, and one worker showed abnormal banding patterns for sis oncogene related proteins. The authors conclude that the abnormal serum oncogene proteins in these workers with known exposure to carcinogens may represent an early marker of neoplastic disease. (Brandt-Rauf et al, 1988)

Study #11

  • half of PCB poisoning victims showed respiratory damage
Studies were conducted on respiratory involvement of 197 patients with Yusho disease. Observations included: signs of chronic bronchitis or pneumonia were found in one-half the patients; signs of secondary infection found in the sputum; and a slight level of occlusion in the terminal airways and a reduction in arterial blood partial oxygen pressure were noted in lung function tests. Effects of giving polychlorinated biphenyls orally with oil to rats and mice were studied. Morphological changes in the lungs of experimental animals were marked in the type II alveolar cells. No morphological changes were noted in the lung surfactants. The alveolar phagocytes showed a picture of consuming lipids containing polychlorinated biphenyls. (Shigematsu et al, 1974)

Study #12

  • The incidence and severity of respiratory symptoms correlated well with the concentration of PCB in the blood and sputa
Clinical, laboratory and pathological findings on respiratory involvement in polychlorinated biphenyl (PCB) poisoning were studied in 401 patients and their pathological changes were produced in rats given PCB orally. Respiratory symptoms included expectoration in 40% of the 289 nonsmoking patients with PCB poisoning and mild wheezing in 2%. The incidence and severity of the respiratory symptoms correlated well with the concentration of PCB in the blood and sputa. Chest roentgenographic findings, pulmonary function tests and pathological findings revealed bronchiolitis in many, and pneumonia or atelectasis in about 1/10 of the patients with reticulo-linear shadows. Peribronchiolar changes may be primarily due to either PCB poisoning or associated infection. Respiratory distress was often exacerbated by viral or bacterial infection persisting for more than a half year in about half of the patients examined. The Ig(immunoglobulin)A and IgM levels in the serum decreased considerably within 2 yr after the onset of the disease and definite decreases in IgA levels may correlate well with the bacterial infection. PCB found in sputa may have been present in association with lipid in type II cells of the lung (or with excretion from bronchial cells) and may have been phagocytosed in alveolar macrophages and may change their phagocytic function. (Shigematsu et al, 1978)

Study #13

  • for 5 years after PCB poisoning, respiratory symptoms persisted in most patients; in patients with high blood PCB levels, signs of chronically infected airways were observed
  • pathologic changes in lungs and thymus were observed in rats, including necrosis of Clara cells, mild pulmonary edema
  • respiratory problems were mainly in small airways and were due primarily to furans [PCBs are usually contaminated with furans]
Respiratory involvement and immune status was studied and followed up for 14 years in 401 patients with polychlorinated-biphenyl (1336363) (PCB) poisoning caused by ingestion of contaminated edible rice-bran-oil. Respiratory symptoms correlated with PCB levels in blood and were often exacerbated by viral or bacterial infection. Symptoms improved gradually but remained after 14 years. Study and follow up included assessment of subjective symptoms, chest x-rays, pulmonary function tests, sputum microbiology, and measurement of immunoglobulin and PCB levels in serum and sputum. Pulmonary function and immunological status observed in February and March of 1983 (11 year follow up) were reported. Approximately 1 year after onset of disease, half of the patients complained of expectoration; these patients had high blood PCB concentrations. In some patients, wheezes without radiological, physiological, or immunological evidence of bronchial asthma or pulmonary emphysema were observed. For 5 years after onset, respiratory symptoms persisted in most patients; in patients with high blood PCB levels, signs of chronically infected airways were observed. PCB levels in blood changed little during the observation period. Pulmonary function was tested in 12 nonsmoking patients; in eight, inspiratory and expiratory rhonchi were audible at all times in 1970 and 1974 (2 to 6 years after disease onset). In 1983, slight improvement was observed and no audible rhonchi were noted. Immunoglobulin-A and immunoglobulin-M levels were decreased, while immunoglobulin-G level was increased in 1970. In 1972, these immunoglobulins were normal except in three patients. In Sprague-Dawley-rats fed polychlorinated dibenzofurans (PCDFs) (0.25 milligrams three times per week for 1 or 2 weeks), pathologic changes in lungs and thymus were observed, including necrosis of Clara cells, mild pulmonary edema, and thymic atrophy, with similar but milder effects noted for PCBs. The authors conclude that respiratory involvement in patients with PCB and PCDF poisoning is located mainly in small airways and is due primarily to PCDFs. (Nakanishi et al, 1985)

Study #14

  • dioxins are known to cause squamous carcinomas of the oropharynx and lungs (certain PCBs are dioxin-like)
Studies involving polychlorinated biphenyls (PCBs) are reviewed. PCBs are a class of halogenated aromatic compounds, including halogenated biphenyls, naphthalenes, dibenzodioxides, and dibenzofurans. PCBs persist in the environment and are retained in tissue because they are lipid soluble. They affect reproduction, suppress the immune system, cause tumors in laboratory rodents, cause hepatic porphyria, and cause chick edema in chickens. Cell mediated immunity is impaired by PCB, although the degree of impairment is determined by the type of isomers present. PCBs are not teratogenic, but they are fetotoxic, producing cleft palates, subcutaneous edema, and hemorrhage. PCBs are passed to mammalian offspring in the milk. 2,3,7,8-Tetrachloro-dibenzo-p-dioxin (1746016) (TCDD) is known to cause hepatocellular carcinomas and squamous carcinomas of the oropharynx and lungs. Subcutaneous sarcomas and tumors of the thyroid are also noted. The primary source of PCB exposure to the general United States population is fish from contaminated water. Serum cholesterol levels in humans are directly proportional to PCB levels. The concentration of PCB in human milk is particularly high. There is no clear evidence of harm to humans from PCB, but research is inconclusive. The author concludes that PCB may be a cancer promoter, but additional studies on exposed human cohorts, such as fishermen, must be done before any conclusions about the effects of PCB on humans can be reached. (Kimbrough, 1985)

Study #15

  • PCB induces enzymes which helps promote mutations caused by oil vapors
The genotoxic effects of oil vapors associated with wok cooking in China were studied in-vitro. Condensates were collected from filters mounted above woks in which the oils were heated to 270 degrees-C. Positive results in a mutation assay with Salmonella-typhimurium strain (TA-98) and Aroclor-1254 induced rat liver S9 were seen using unrefined rapeseed oils (URSO), refined rapeseed oils, and soybean oils. The addition of 0.1% or more butylated-hydroxyanisole (BHA) to the URSO prior to heating inhibited its mutagenic effects. Hydrogenation of rapeseed oil also eliminated its mutagenic effect. URSO condensates were determined to be mutagenic in the SV50 forward mutation assay as well and these oils induced increased numbers of sister chromatid exchanges in V79-Chinese-hamster cells compared with controls. The addition of BHA or oil hydrogenation resulted in a decrease in the number of sister chromatid exchanges. A dose dependent increase in the number of polychromatic erythrocytes with micronuclei was seen in mice injected with URSO condensates; this increase was inhibited with the use of URSO condensates. The authors conclude that the high incidence of lung cancer seen in females in China may be due to exposure to cooking oil emissions. (Qu et al, 1992)

Study #16

  • several epidemiologic studies on the carcinogenicity of PCBs in both occupational exposure and accidental intoxication suggest that PCBs might be a potent carcinogen in the lung.
  • PCBs have been reported to promote lung tumors
  • certain types of PCBs associated with cancer also increase cytochrome P-450-dependent monooxygenases, which are abundant in bronchiolar (lung) Clara cells
  • PCBs may promote tumors by inhibiting intercellular communication and/or by stimulating cell proliferation
  • furans induce necrosis (cell death) and epoxide formation to their target cells, which might result in lung cancer [PCBs are usually contaminated with furans]
PCBs are compounds whose physical/chemical properties led to their wide spread commercial use. The persistence and stability of PCBs have resulted in a worldwide distribution. PCDFs, ones of PCB derivatives, are primary causal agents of mass food poisoning, called Yusho in Japan and Yu-Cheng in Taiwan. Several epidemiologic studies on the carcinogenicity of PCBs in both occupational exposure and accidental intoxication suggest that PCBs might be a potent carcinogen in liver and lung. Many investigators reported that PCBs induced hepatocellular carcinoma in rat and mice. Although either mutagenic or genotoxic effects of PCBs are not definite, their tumor promoting effects have been repeatedly demonstrated in the liver. The effects of PCBs as tumor promoter in the lung have also been reported. PCB congeners that efficaciously promote carcinogenesis increase cytochrome P-450-dependent monooxygenases, which are abundant both in bronchiolar Clara cells and in hepatocytes. PCB congeners which are inducers of P-450 may be active as tumor promoters by inhibiting intercellular communication and/or by stimulating cell proliferation. Furan derivatives like PCDFs have high affinity to bronchiolar Clara cells and hepatocytes. PCDFs induce necrosis and epoxide formation to their target cells, which might result in carcinogenesis of liver and lung. (NAKANISHI et al, 1991)

Study #17

  • PCBs stimulate production of lung macrophages
Samples of human epithelial lining fluid and a variety of pulmonary alveolar macrophage (PAM) preparations were tested for their ability to reduce hexavalent chromium (7440473) (Cr-VI), and were compared with preparations of other human or adult Sprague-Dawley rat cells. The patterns of this reaction and other biochemical parameters were examined and related to smoking habits; its inducibility by Aroclor-1254 (11097691) was evaluated in rat pulmonary alveolar macrophages. Preparations of PAM obtained from 47 subjects were shown to reduce Cr-VI and decrease its mutagenicity; specific activity was significantly higher than in preparations of mixed cell populations from human peripheral lung parenchyma or bronchial tree, or from rat lung or liver. In smokers, at equivalent numbers of pulmonary alveolar macrophages, Cr-VI reduction, total protein and oxidoreductase activities were significantly reduced; there were no significant variations between lung cancer and noncancer patients. In rats, the Cr-VI reducing activity of pulmonary macrophage preparations was generally induced by Aroclor-1254. The epithelial lining fluid also displayed some Cr-VI reduction. The authors conclude that alveolar macrophages represent an important aspecific defense mechanism and in some cases also possess metabolic systems capable of the intracellular detoxification of direct-acting chemicals. (Petrilli et al, 1986)

Study #18

  • several chemicals (including tobacco constituents) were mutagenic or more mutagenic in the presence of lung enzymes induced by PCBs
  • enzymes may increase the lung cancer risk from these chemicals
The mutagenicity of N-nitrosopropylamines was investigated in-vitro. The mutagenic potential of N-nitroso(2-hydroxypropyl)(2-oxopropyl)amine (61499283) (HPOP), N-nitrosobis(2-oxopropyl)amine (6059934) (BOP), N-nitrosomethyl(2-oxopropyl)amine (55984515) (MOP), N-nitrosomethyl(2-hydroxypropyl)amine (75411835) (MHP), N-nitrosobis(2-hydroxypropyl)amine (53609646) (BHP), N-nitrosobis(2-acetoxypropyl)amine (6041481) (BAP), and N-nitroso-2,6-dimethylmorpholine (1456286) (NDMM) were evaluated in the Amesalmonella assay using strain TA-100 in the presence or absence of lung and pancreas 9,000 times the force of gravity (9,000G) S9 fractions from rats, hamsters, mice, rabbits, monkeys, and humans. The S9 fractions were obtained from untreated or polychlorinated biphenyl (PCB) induced animals. HPOP, MOP, and BOP showed positive responses in the presence of lung S9 from all species. HPOP, MOP, BOP, and MHP were mutagenic in the presence of lung S9 from PCB induced rats, hamsters, and mice. In the presence of pancreas S9 from uninduced or PCB treated animals, only HPOP and BOP were mutagenic. BHP, BAP, and NDMM showed negative responses under all conditions. The mutagenicity of MHP, BOP, and MOP was evaluated in the presence of lung S9 from PCB treated rats, hamsters, and mice after preincubation in an atmosphere of carbon-monoxide (630080) or after addition of cytochrome-c, metyrapone (54364), or 7,8-benzoflavone (604591). Carbon-monoxide, cytochrome-c, and metyrapone completely inhibited the mutagenic activity of MHP, but had no effect on that of MOP or BOP. 7,8-Benzoflavone had no effect on mutagenic activity of MOP, BOP, or MHP. The authors conclude that only the methyl derivatives of N-nitrosopropylamines, MHP and MOP, are activated by the lung from five animal species and humans. The results provide the first evidence of activation of N-nitrosopropylamine by human lung S9. Further studies are necessary to assess the cancer risk to humans posed by these compounds. (Mori et al, 1986)

Study #19

  • humans exposed to complex combustion mixtures will have higher DNA adduct levels in lung cells
  • adduct levels depend on the genotoxic and DNA adduct-forming potency of the mixture
DNA adducts derived from complex mixtures of polycyclic aromatic compounds emitted from tobacco smoke are compared to industrial pollution sources (e.g., coke ovens and aluminum smelters), smoky coal burning, and urban air pollution. Exposures to coke oven emissions and smoky coal, both potent rodent skin tumor initiators and lung carcinogens in humans, result in high levels of DNA adducts compared to tobacco smoke in the in vitro calf thymus DNA model system, in cultured lymphocytes, and in the mouse skin assay. Using tobacco smoke as a model in human studies, we have compared relative DNA adduct levels detected in blood lymphocytes, placental tissue, bronchoalveolar lung lavage cells, sperm, and autopsy tissues of smokers and nonsmokers. Adduct levels in DNA isolated from smokers were highest in human heart and lung tissue with smaller but detectable differences in placental tissue and lung lavage cells. Comparison of the DNA adduct levels resulting from human exposure to different complex mixtures shows that emissions from coke ovens, aluminum smelters, and smoky coal result in higher DNA adduct levels than tobacco smoke exposure. These studies suggest that humans exposed to complex combustion mixtures will have higher DNA adduct levels in target cells (e.g., lung) as compared to nontarget cells (e.g., lymphocytes) and that the adduct levels will be dependent on the genotoxic and DNA adduct-forming potency of the mixture. (Lewtas et al, 1993)

Study #20

  • PCBs showed a significant excess of all cancers
  • one study showed statistically significant increased human mortality from all malignancies (33 observed, 15.5 expected), including from lung cancer (8 observed, 2.5 expected).
  • second study showed intragastric administration of PCBs to mice increased the incidence of lung tumours induced by intraperitoneal administration of N-nitrosodimethylamine (a tobacco chemical).
A. Evidence for carcinogenicity to humans (limited) Information on the possible carcinogenic risk of human exposure to polychlorinated biphenyls (PCBs) comes from studies of occupational populations and of populations exposed to the compounds accidentally. PCB mixtures may be contaminated with polychlorinated dibenzofurans and polychlorinated dibenzodioxins (see, e.g, p. 350). A slight increase in the incidence of cancer, particularly melanoma of the skin, was reported in a small group of men exposed to Aroclor 1254, a mixture of PCBs. In a study of over 2500 US workers exposed to a similar mixture of PCBs during the manufacture of electrical capacitors, five deaths due to cancer of the liver and biliary passages were observed, where as 1.9 would have been expected. This increase was sustained mainly by female workers in one of the two plants in the study (four of the five deaths), and all five workers had first been employed before the early 1950s. Another study of workers in a capacitor plant was conducted in Italy. Exposure in the early years of production (until 1964) was to PCB mixtures containing 54% chlorine (mainly Aroclor 1254 and Pyralene 1476), which were later replaced by mixtures containing 42% chlorine (mainly Pyralene 3010 and 3011). Early results showed a significant excess of all cancers among male workers, which was due mainly to cancers of the digestive system and of the lymphatic and haematopoietic tissues. Among female workers, a slight increase in mortality from cancer of the lymphatic and haematopoietic tissues was reported. The study was later enlarged and extended to include 2100 workers and to cover the period 1946-1982. Both male and female workers exhibited significantly increased cancer mortality in comparison with rates for the local population (14 observed, 7.6 expected; and 12 and 5.3, respectively, for men and women). Among male workers, cancers of the gastrointestinal tract (two stomach, two pancreas, one liver and one biliary passages) taken together were significantly increased (6 observed, 2.2 expected). Female workers showed a significant increase in deaths from haematological neoplasms (4 observed, 1.1 expected). In Sweden, among 142 male workers employed between 1965 and 1978 in a capacitor manufacturing plant when PCB mixtures containing up to 42% chlorine had been used, no significant excess of cancer deaths was noted. Cancer incidence was also examined: the number of cases observed corresponded well to that expected. One individual in a subgroup with higher exposure developed two relatively rare tumours, both of which occurred ten years after the start of exposure: a slow-growing mesenchymal tumour (desmoid) and a malignant lymphoma. After contamination of cooking oil with a mixture of PCBs (Kanechlor 400) in Japan in 1968, a large population was intoxicated ('Yusho' disease). An early report on mortality from 1963-1983 showed a significantly increased risk of all cancers, and an almost five-fold significantly elevated risk of primary liver cancer. The edible rice oil had also been contaminated by polychlorinated quaterphenyls and polychlorinated dibenzofurans. Dose response relationships were not clarified. A further comprehensive study of 887 male 'Yusho' patients showed statistically significantly increased mortality from all malignancies (33 observed, 15.5 expected), from liver cancer (9 observed, 1.6 expected) and from lung cancer (8 observed, 2.5 expected). Use of local rather than national rates in calculating expected number of deaths decreased the observed:expected ratio for liver cancer from 5.6 to 3.9, which was still statistically significant. A closer look at the geographical distribution of liver cancer cases did not allow exclusion of factors other than PCB poisoning as a possible explanation for this finding. For the 874 female patients examined, none of the noted observed:expected ratios was significant. In a series of ten autopsies of 'Yusho' patients, two adenocarcinomas of the liver were found, with no indication of a direct association with exposure to PCBs. Ultrasonic and tumour marker examination of two series of 79 and 125 patients with 'Yusho' disease in 1983 and 1984, respectively, did not reveal any case of hepatic-cell carcinoma. Two studies of the PCB content of fat tissues and cancer occurrence were available. An association was suggested between PCB concentrations in subcutaneous abdominal adipose tissue and the occurrence of cancers of the stomach, colon, pancreas, ovaries and prostate. No indication emerged of a relationship between PCB content in extractable breast fat tissue and the occurrence of breast cancer. The available studies suggest an association between cancer and exposure to PCBs. The increased risk from hepatobiliary cancer emerged consistently in different studies. Since, however, the numbers were small, dose-response relationships could not be evaluated, and the role of compounds other than PCBs could not be excluded, the evidence was considered to be limited. B. Evidence for carcinogenicity to animals (sufficient) Certain PCBs (particularly with greater than 50% chlorination) produced benign and malignant liver neoplasms in mice and rats after their oral administration. Oral administration of Aroclor 1254 to rats yielded hepatocellular adenomas and carcinomas as well as intestinal metaplasia and a low, statistically nonsignificant incidence of stomach adenocarcinomas. PCBs were inadequately tested in mice for induction of skin tumours. In several studies, oral or intraperitoneal administration of PCBs enhanced the incidences of preneoplastic lesions and of neoplasms of the liver induced in rats by N-nitrosodiethylamine or 2-acetylaminofluorene. In one study, intragastric administration of PCBs to mice increased the incidence of lung tumours induced by intraperitoneal administration of N-nitrosodimethylamine. C. Other relevant data No data were available on the genetic and related effects of PCBs in humans. Dominant lethal effects were not induced in rats administered PCBs orally, but were produced in rats nursed by females that had received PCBs orally. PCBs did not induce chromosomal aberrations in bone-marrow cells or spermatagonia of rats treated in vivo; micronuclei were not induced in bone-marrow cells of mice in one study, while equivocal results were obtained in a second study in which the PCBs were administered in corn oil. They did not transform Syrian hamster embryo cells in vitro. PCBs induced DNA strand breaks and unscheduled DNA synthesis in rat hepatocytes in vitro. Neither chromosomal breakage nor aneuploidy was induced in Drosophila. PCB mixtures did not induce SOS repair and were not mutagenic to bacteria. 2,2',5,5'-Tetrachlorobiphenyl induced DNA strand breaks in mouse cells in vitro. 2,4,5,2',4',5'-Hexachlorobiphenyl but not 3,4,5,3',4',5'-hexachlorobiphenyl inhibited intercellular communication in Chinese hamster V79 cells. Purified 2,4,2',4'-, 2,5,2',5'- and 3,4,3',4'-tetrachloro- and 2,4,6,2',4',6'-hexachlorobiphenyl were not mutagenic to bacteria. (IARC - International Agency for the Research of Cancer)

Study #21

  • PCB induced enzymes may alter the metabolism and the pattern of DNA adducts formed in human lung tissue as a result of certain carcinogenic pollutants
It has previously been shown that 6-nitrochrysene can be activated to electrophilic species capable of reacting with DNA through metabolic pathways that form N-hydroxy-6-aminochrysene or trans-1,2-dihydroxy-1,2-dihydro-6-aminochrysene as critical intermediates. Since the lung is a known target tissue for the carcinogenic action of polycyclic nitroaromatic hydrocarbons, we investigated the metabolism and DNA binding of [3H]6-nitrochrysene in 11 specimens of human bronchus. Analysis of medium from [3H]6-nitrochrysene-treated explants indicated the presence of trans-9,10-dihydroxy-9,10-dihydro-6-nitrochrysene (0.04-330 pmol/mg epithelial DNA), trans-1,2-dihydroxy-1,2-dihydro-6-nitrochrysene (12-1700 pmol/mg epithelial DNA), 6-aminochrysene (1.6-2200 pmol/mg epithelial DNA), and trans-1,2-dihydroxy-1,2-dihydro-6-aminochyrsene (3.6-610 pmol/mg epithelial DNA). Both the levels and the relative proportions of these metabolites varied widely in explants from different individuals. The amount of DNA recovered and the level of DNA modification were sufficient for adduct analysis in eight of the 11 cases for which metabolite data were obtained. Five additional bronchial specimens for which metabolite data were not obtained were also analyzed for carcinogen-DNA adducts. The levels of binding varied from 0.06 to 30.5 pmol [3H]6-nitrochrysene bound/mg DNA (two adducts per 10(8) nucleotides-10 adducts per 10(6) nucleotides). HPLC analyses of enzymatic hydrolysates of the explant DNA indicated that 11 of 13 cases contained adducts with retention times identical to those of adducts derived from trans-1,2-dihydroxy-1,2-dihydro-6-aminochrysene or N-hydroxy-6-aminochrysene. The adduct derived from trans-1,2-dihydroxy-1,2-dihydro-6-aminochrysene was the major adduct detected in eight of 13 cases. The reasons for the variation in metabolism and adduct formation observed in [3H]6-nitrochrysene-treated explants of bronchus from different donors are not known but may reflect differences in the activities of enzymes responsible for the metabolism of this compound. The influence of induction of drug metabolizing enzymes on the activation pathway of 6-nitrochrysene in an intact cell system was tested using rat hepatocytes. 6-Nitrochrysene was incubated with freshly isolated hepatocytes from rats that were either untreated or pretreated with phenobarbital, 3-methylcholanthrene or Aroclor 1254. Although the levels of adducts were similar in all cases, the pattern of DNA adducts formed in these hepatocytes was dependent on the nature of the pretreatment of the rats. As previously reported, hepatocytes from untreated rats contained adducts derived from N-hydroxy-6-aminochrysene. (Delclos et al, 1989)

lung cancer research, lung cancer studies, lung research, lung studies, lung tumor research, lung tumor studies

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    lung cancer research, lung cancer studies, lung research, lung studies, lung tumor research, lung tumor studies