PMCCPMCCPMCC

Search tips
Search criteria 

Advanced

 
Logo of nihpaAbout Author manuscriptsSubmit a manuscriptNIH Public Access; Author Manuscript; Accepted for publication in peer reviewed journal;
 
Cancer Epidemiol Biomarkers Prev. Author manuscript; available in PMC May 1, 2011.
Published in final edited form as:
PMCID: PMC2866160
NIHMSID: NIHMS186815
Elevated Levels of Volatile Organic Carcinogen and Toxicant Biomarkers in Chinese Women Who Regularly Cook at Home
Stephen S. Hecht,1* Adeline Seow,2 Mingyao Wang,1 Renwei Wang,1 Lei Meng,1 Woon-Puay Koh,2 Steven G. Carmella,1 Menglan Chen,1 Shaomei Han,1 Mimi C. Yu,1 and Jian-Min Yuan1,3
1Masonic Cancer Center, University of Minnesota, Minneapolis, Minnesota, USA
2Department of Epidemiology and Public Health, Yong Loo Lin School of Medicine, National University of Singapore, Singapore
3Division of Epidemiology and Community Health, School of Public Health, University of Minnesota, Minneapolis, USA
*To whom correspondence should be addressed: Masonic Cancer Center, University of Minnesota, MMC 806, 420 Delaware St SE, Minneapolis, MN 55455, USA. phone: (612) 624-7604 fax: (612) 626-5135 ; hecht002/at/umn.edu
Background
Epidemiologic studies associate lung cancer in non-smoking Chinese women with Chinese-style wok cooking. Our goal was to quantify carcinogen and toxicant biomarkers in Chinese women who reported regularly doing home cooking compared to women randomly selected from the Singapore Chinese Health Study as controls.
Methods
Biomarkers were quantified by high performance liquid chromatography-mass spectrometry (HPLC-MS), HPLC-with fluorescence detection, and gas chromatography-mass spectrometry.
Results
Compared with controls, women who engaged in regular home cooking had significantly higher levels of mercapturic acids of acrolein [geometric mean 1959 pmol/mg creatinine (95% CI 1554–2467) vs.1370 (95% CI 1077–1742), P = 0.038], crotonaldehyde [geometric mean 232 pmol/mg creatinine (95% CI 193–277) vs. 142 (95% CI 118–171) P = 0.0004], and benzene [geometric mean 0.58 pmol/mg creatinine (95% CI 0.44–0.78) vs. 0.18 (95% CI 0.14–0.24) P < 0.0001]. No significant differences were found in levels of mercapturic acids of 1,3-butadiene, pyrene and phenanthrene metabolites, or acetaldehyde-leukocyte DNA adduct levels between the groups. Levels of the ethylene oxide mercapturic acid were significantly higher in the controls.
Conclusions
The higher levels of the mercapturic acid of benzene, a multi-organ carcinogen, in the women who cooked are particularly notable. Overall, the results showing increased exposure to the volatile toxicants and carcinogens acrolein, crotonaldehyde, and benzene in Chinese women who regularly cook provide a plausible lead for further investigating the role of volatile compounds generated during high temperature cooking with oils as causes of lung cancer.
Impact
A new direction for research on lung cancer etiology is suggested.
Keywords: Carcinogen biomarkers, wok cooking, lung cancer
Chinese women in Asia have higher rates of lung cancer than in many other places in the world. In China, the age standardized incidence rate for female lung cancer is 19.9 per 100,000, and in Singapore it is 17.5 while rates are far lower (1.5 – 9.2) in countries such as Vietnam, Indonesia, India, and Russia (1,2). Cigarette smoking is definitely not the major risk factor for lung cancer in these women, nor is there strong evidence implicating secondhand smoke exposure (3). In some parts of China, use of solid fuels for heating in poorly ventilated spaces is considered a cause of lung cancer (4). However, a more common cause may be Chinese-style cooking. Multiple epidemiologic studies document an association between lung cancer in Chinese women and Chinese-style cooking with oils heated at high temperatures (311). In one recent study, a strong link was observed between lung cancer risk and cooking dish-years, a measure of lifetime cooking by stir frying, deep frying, or frying in a wok, common in Chinese households (3). A working group of the International Agency for Research on Cancer (IARC) concluded that emissions from high temperature frying are “probably carcinogenic to humans (Group 2A)” (4).
Several studies have analyzed fumes generated during high temperature cooking with various oils. A variety of carcinogens and toxicants have been detected in the fumes including acetaldehyde, acrolein, various higher aldehydes, benzene, 1,3-butadiene, ethylene oxide, and polycyclic aromatic hydrocarbons (PAH) (1216). Benzene, 1,3-butadiene, ethylene oxide, and a representative PAH, benzo[a]pyrene, are considered carcinogenic to humans by IARC while acetaldehyde is classified as possibly carcinogenic to humans (1721). Acrolein, a well known toxicant and cilia-toxic agent, is rated as not classifiable for carcinogenicity (22).
There are no reports of biomarker studies to assess carcinogen and toxicant uptake in Chinese women who regularly cook at home. Therefore, in this study we determined levels of biomarkers of exposure to acrolein, crotonaldehyde, benzene, 1,3-butadiene, ethylene oxide, acetaldehyde and PAH in non-smoking, non-alcohol drinking Chinese women from Singapore who reported doing home cooking five or more days per week and in Chinese women who were randomly chosen among the participants of the population-based Singapore Chinese Health Study.
Study Design
Forty-two women volunteers who enrolled in a study on food mutagens (23) constituted one group of ‘regular cooks’ in this study. The subjects were identified using a combination of purposive sampling and ‘snowballing’. Criteria for participation were that they should be Singapore residents, of Chinese ethnicity, non-smokers, and that they cooked regularly at home five or more days a week. All women were asked to consume 2–4 cups of coffee the preceding afternoon and to abstain from painkillers and chocolate for two days, to allow measurement of the caffeine metabolic ratio, which was used in a separate study (23). When research staff visited the home, a structured questionnaire was administered and a 20 ml sample of blood was drawn by venipuncture. This sample collected from 42 nonsmoking and nondrinking women was used for the acetaldehyde-leukocyte DNA adduct analysis.
Because the above group had consumed coffee, which we thought could interfere with the urinary biomarker analyses of exposure to PAH, we recruited a second group of women who regularly performed wok cooking, and collected single-void spot urine samples at randomly timed points from these women. Using the same recruitment and sampling method as the first group, we recruited 54 women in August 2009. The criteria for the present study were Chinese ethnicity, citizens or permanent residents of Singapore who cooked regularly at home five or more days a week, but neither smoked cigarettes nor drank coffee or alcoholic beverages.
As the comparison group (general population controls) for the present study, 50 women were randomly chosen from the subset of non-smoking, non-alcohol drinking female participants of the Singapore Chinese Health Study, a population-based cohort study of Chinese adults initiated in 1993. The cohort included 63,257 Chinese men and women (representing 85% of eligible subjects) belonging to the two major dialect groups (Cantonese, Hokkien) of Chinese in Singapore. The subjects, who were 45–74 years of age and resided in government-built housing estates comprising 86% of all residents resided, were enrolled between April 1, 1993 and December 31, 1998. At the time of recruitment, each subject was interviewed in person by a trained interviewer using a structured questionnaire that requested information on demographics, lifetime use of tobacco, current consumption of alcoholic beverages, current physical activity, menstrual and reproductive histories (women only), occupational exposure, medical history, and family history of cancer. Information regarding dietary habits during the past 12 months was obtained using a validated food frequency questionnaire (24). We requested blood (or buccal cells if blood donation was refused) and single-void spot urine specimens from a random 3% sample of cohort participants between April 1994 and December 1999. Beginning in January 2000, request for biospecimens was extended to all surviving members of the cohort. During the same time, a follow-up survey conducted by telephone brought up to date subjects’ histories on use of tobacco and alcohol, medical and medication histories, and for women, menopausal status and lifetime use of replacement hormones. By April 2005, all surviving cohort subjects had been contacted for biospecimen donation. Samples were obtained from 32,535 participants, representing 61% of eligible subjects. These 50 women were chosen among the 12,600 non-smoking, non-alcohol drinking women who had donated both blood and urine samples.
Singapore is a small city-state country, located one degree north of the equator and has tropical weather year around. Therefore there is no need for the use of heating systems in houses or apartments. Windows, especially those in the kitchen, are usually open for ventilation during cooking.
Both buffy coat and urine specimens from each chosen subject were retrieved from storage in −80°C freezers at the National University of Singapore and shipped in boxes packed with dry ice to the University of Minnesota, where the laboratory measurement took place. The Institutional Review Boards at the University of Minnesota and the National University of Singapore approved the study.
Biomarker Analyses
Urinary mercapturic acid metabolites of the following were quantified: for acrolein [3-hydroxypropyl mercapturic acid (HPMA)]; for crotonaldehyde [4-hydroxybut-2-yl mercapturic acid (HBMA)]; for benzene [S-phenyl mercapturic acid (SPMA)]; for 1,3-butadiene [1-hydroxy-2-(N-acetylcysteinyl)-3-butene and 1-(N-acetylcysteinyl)-2-hydroxy-3-butene, collectively called MHBMA for monohydroxybutyl mercapturic acid]; and for ethylene oxide (N-acetylcysteinyl)ethanol, also called 2-hydroxyethyl mercapturic acid (HEMA)]. Urinary 1-hydroxypyrene (1-HOP) and r-1,t-2,3,c-4-tetrahydroxy-1,2,3,4-tetrahydrophenanthrene (PheT), metabolites of the PAH pyrene and phenanthrene, were also quantified. As a measure of exposure to acetaldehyde, leukocyte DNA adducts were measured. The analyses for the mercapturic acids (25), 1-HOP (26), and PheT (27,28) were carried out essentially as described previously.
The analysis for the acetaldehyde-DNA adduct N2-ethylidene-dG (as N2-ethyl-dG) was similar to that described previously (29), but modified for analyzing small amounts of DNA. The buffy coat samples were diluted with PBS buffer (1:3 V/V) to 1 ml and stored in 2 plastic straws (each with 0.5 ml) in a −80 °C freezer until use. DNA isolation was carried out using the Puregene DNA purification protocol (Qiagen, Valencia, CA) with modifications. Buffy coat samples were thawed at room temperature, then transferred into 15 ml centrifuge tubes, followed by addition of 3.0 ml of RBC lysis solution into each tube. The cell lysate was centrifuged and the supernatant was discarded. The white blood cell pellet was suspended by vortexing, and 300 µl of cell lysis solution and 1 µl of proteinase K (20 mg/ ml) were added to the mixture. One µl of RNase I (4 mg/ml) was added to the cell lysate on the next day and the mixture was incubated for 2 h at room temperature. After adding 250 µl of protein precipitation solution, the mixture was centrifuged to remove protein. DNA was precipitated from the supernatant by adding 750 µl of ice cold isopropanol. The clumped DNA was washed with 100% ethanol and dried under a stream of N2. The DNA was stored at −30 °C until analysis.
DNA samples were dissolved in 400 µl of 10 mM Tris/5mM MgCl2 buffer containing [15N5]N2-ethyl-dG (50 fmol) and NaBH3CN (10 mg). The pH was adjusted to 7 with 10 µl of 0.1N HCl, and the DNA was digested overnight at room temperature with 650 units of DNase I (type II, from bovine pancreas). Then to the resulting mixture were added 650 additional units of DNase I, 0.03 units of phosphodiesterase I (type II, from Crotalus adamanteus venom), and 240 units of alkaline phosphatase. The mixture was incubated at 37 °C for 70 min and then allowed to stand overnight at room temperature. Enzymes were removed by centrifugation using a centrifree MPS device (MW cutoff of 30,000; Amicon, Beverly, MA). The hydrolysate, after removal of a 10 µl aliquot for dG analysis, was desalted and purified using a solid phase extraction cartridge [Strata-X 33 µm, 30 mg/1 ml (Phenomenex)]. The cartridge was washed with H2O, 10% CH3OH, and 1 ml of 70% CH3OH in H2O. The 70% CH3OH fraction was collected and evaporated to dryness, dissolved in H2O, and purified using a mixed mode, anion exchange reversed phase extraction cartridge (Oasis MAX, 30 mg/cartridge, Waters). The pH of the sample was adjusted to >12 by addition of 20 µl of 0.2N KOH, and applied to the cartridge, which had been equilibrated with 0.2N KOH. The cartridge was washed with 0.01N KOH, 0.01N KOH in CH3OH, H2O, 1M ammonium acetate (pH 6.8), H2O, and 10% CH3OH. Adducts were eluted with 70% CH3OH, and the solution was evaporated to dryness. The residue was dissolved in 20 µl of H2O, and analyzed by LC-ESI-MS/MS. We used an Agilent 1100 HPLC system with a 150 mm × 0.5 mm 4µm Polar RP column (Phenomenex, Torrance, CA) and a Discovery Max (Thermoelectron, San Jose, CA) triple quadrupole mass spectrometer. Solvent A was ammonium acetate and solvent B was methanol. The column temperature was maintained at 50 °C. The gradient started with 5% B and increased to 22% B in 20 min and then was ramped to 80% in 5 min. The flow rate was 10 µl/min. The column was flushed with 100% B for 10 min and then equilibrated under the initial conditions for 15 min. The ESI source was operated in the positive ion mode and the MS parameters were set as follows: voltage, 3.8 kV; current, 3 µA; and heated ion transfer tube, 275 °C. The collision energy was 12eV and the Ar collision gas pressure was 1.0 mTorr.
Quantitation of dG was performed by HPLC using a 250 mm × 0.5 mm 5µm Luna, C18(2) column (Phenomenex). Solvent A was H2O and solvent B was CH3OH. The gradient started with 5% B and increased to 22% B in 20 min, and then was ramped to 80% B in 5 min. The flow rate was 10 µl/min. The column was then equilibrated under the initial conditions for 15 min.
Buffer blanks containing internal standard were processed as above and analyzed to check the baseline and possible contamination. Calf thymus DNA (50 µg) with internal standard added as above was used as a positive control to determine inter-day precision and accuracy. Each set of samples was run together with buffer blanks and positive controls. Of the 42 samples, the assay failed on 3 samples. Therefore we reported results of N2-ethylidene-dG on 39 women cooks only.
Creatinine was assayed by the University of Minnesota Medical Center (Fairview) Diagnostic Laboratories (Minneapolis, MN) using Vitros CREA slides.
Statistical Analyses
The χ2 test and the t-test were used to compare the distributions of selected variables between Chinese women who did home cooking 5 or more days per week (‘Daily cooks’) and a random sample of Chinese women from the Singapore Chinese Health Study (‘population controls’). Urinary levels of PheT, 1-HOP, and the individual mercapturic acids HPMA, HBMA, SPMA, MHBMA and HEMA were expressed in units of pmol/mg creatinine to correct for varying water contents of individual spot urine samples while the level of the acetaldehyde-DNA adduct N2-ethylidene-dG (measured as N2-ethyl-dG) was in fmol/µmol dG. We also summed all measured mercapturic acid metabolites (i.e., HPMA, HBMA, SPMA, MHBMA and HEMA) to represent the overall level of exposure to the volatile carcinogens and toxicants through home cooking. The summed values were analyzed in the same way as the individual mercapturic acid biomarkers. In addition, we created another unweighted summed index for the overall level of exposure to reduce the dominant effect of one biomarker with high concentration (i.e., the acrolein metabolite – HPMA) over other biomarkers due to their huge difference in urinary concentrations. For this unweighted index, we first assigned to each of the five mercapturic acid metabolites a rank score to each individual among all women: the smallest rank score (i.e. one) was assigned to an individual with the lowest concentration of a given biomarker whereas the largest score was assigned to the one with the highest concentration of the biomarker. We then added the rank scores over the five mercapturic acid metabolites for a given individual, which gave an equal weight to each of the five mercapturic acid metabolites regardless of their actual values. The distributions of all biomarkers measured were markedly skewed toward high values, which were corrected to a large extent by transformation to logarithmic values. Therefore, formal statistical testing was performed on logarithmically transformed values, and geometric (as opposed to arithmetic) means are presented. The analysis of covariance (ANCOVA) method (30) was used to examine the difference in biomarker levels between the daily cooks and the population controls with age as a covariate while the difference in unweighted summed indices between the two groups was examined using the Mann-Whitney test (30). We further assessed the association between home cooking and elevated biomarker levels by means of the odds ratio (OR), and its corresponding 95% confidence interval (CI) and P-value using the logistic regression method (31). Women were grouped into tertiles according to the distribution of a given biomarker or summed indices among the population controls except for HBMA and SPMA. The cutoffs of tertiles for these two biomarkers were based on their distributions of both cooks and population controls to have sufficient number of subjects in each tertile for the calculation of OR since cooks had much higher levels of HBMA and SPMA in their urine. The lowest tertile level was defined as the reference category (OR=1.0). For a given biomarker, elevated ORs (i.e., greater than 1.0) associated with the second and third tertiles would indicate that women who cooked daily were more likely to exhibit high levels of the biomarker relative to their general population counterparts.
Statistical analyses were carried out using SAS software version 9.1 (SAS Institute, Cary, NC). All P-values reported are two-sided, and those that were less than 0.05 were considered to be statistically significant.
The mean age (± standard deviation) of the 54 cooking women who provided samples for the urinary biomarkers was 62.1 (±8.4) years. The corresponding figure for the 50 general population controls was 61.8 (±7.8) years. The mean body mass indices of these daily cooking and control women were 23.7 (±3.5) and 23.6 (±3.3), respectively. These daily cooks had a higher level of education (42.6% with secondary school or higher) than the random control women (30.0% with secondary school or higher). The mean age of the 39 women cooks who gave blood samples was 51.7 (± 10.3) years and their mean body mass index was 24.8 ± 4.4. The mean BMI was comparable with the comparison women while the mean age was younger than the control group. They had a higher level of education (64.3% with secondary school or higher) than the randomly selected control women.
The results of the biomarker analyses, adjusted for age at sample collection, are summarized in Table 1. Statistically significant, higher levels of HPMA from acrolein [geometric mean 1959 pmol/mg creatinine (95% CI 1554–2467) vs.1370 (95% CI 1077–1742), P = 0.038], crotonaldehyde [geometric mean 232 pmol/mg creatinine (95% CI 193–277) vs. 142 (95% CI 118–171) P = 0.0004], and benzene [geometric mean 0.58 pmol/mg creatinine (95% CI 0.44–0.78) vs. 0.18 (95% CI 0.14–0.24) P < 0.0001] were observed in the urine of the daily cooks compared to the random controls. Women who did frequently home cooking also showed statistically significantly elevated levels of summed mercapturic acid metabolites (geometric mean 2476 pmol/mg creatinine (95% CI 1940–3158) vs. 1622 pmol/mg creatinine (95% CI 1281–2053) P = 0.016), and elevated summed rank scores (median score 284 vs. 224, P = 0.002). There were no differences in levels of the urinary biomarkers MHBMA from 1,3-butadiene, 1-HOP from pyrene, PheT from phenanthrene, or N2-ethylidene-dG from acetaldehyde. Levels of urinary HEMA from ethylene oxide were significantly lower in the daily cooks than in the random controls [20.1 pmol/mg creatinine (95% CI 18.4–24.7) vs. 28.3 (95% CI 23.1–34.7) P = 0.02].
Table 1
Table 1
Geometric means of biomarker levels in women who did frequent home cooking (daily cooks) vs. women randomly selected from the Singapore Chinese Health Study (Random controls)a,b
The data are presented by tertiles of the study variables in Table 2. Statistically significant trends of increasing biomarker levels with daily cooking were observed for all of the biomarkers for which significant differences were seen in Table 1. Relative to the general population controls, daily cooks were significantly more likely to fall into the highest tertile category of urinary HPMA, HBMA, and SPMA. The association between the summed values or rank scores of all five mercapturic acid metabolites and frequent home cooking also was statistically significant. When compared with the lowest tertile of summed rank score, ORs (95% CIs) for the second and third tertile of summed rank scores associated with being frequent home cooking were 5.91 (1.41–24.7) and 9.75 (2.45–38.91), respectively (P for trend = 0.001). A slightly inverse relationship was observed for PheT, and none of the other biomarkers was significantly associated with cooking status.
Table 2
Table 2
Odds ratios (95% confidence intervals) of women who did frequent home cooking relative to women in a random sample of the Singapore Chinese Health Study associated with elevated biomarker levels by tertilesa
The results of this study provide a plausible lead for understanding epidemiologic studies that show a higher risk of lung cancer in nonsmoking women who regularly cook with high temperature oils (311). Significantly higher levels of mercapturic acid biomarkers of the volatile organic carcinogens and toxicants acrolein, crotonaldehyde, and benzene were observed in the women who cooked compared to controls. These results provide an initial biochemical link between previous studies demonstrating the presence of these compounds in cooking oil fumes (1216) and the epidemiologic studies of lung cancer. Many other volatile organic compounds, some of which may have toxic properties, have been detected in cooking oil fumes (13,14), and our results suggest that uptake of these volatiles might also be increased during wok cooking, although biomarkers for most of them are not available.
Our finding of elevated levels of SPMA, a biomarker of benzene uptake, in the urine of women who cooked is particularly interesting. Levels of this biomarker were approximately 3 times greater in the women who cooked than in controls. Benzene is considered carcinogenic to humans by the U.S. Dept. of Health and Human Services and by the International Agency for Research on Cancer (32,33). The most common finding in epidemiologic studies of benzene exposure is increased risk for leukemia, and benzene is considered a known human leukemogen. However, one large study of industrial exposure carried out in China demonstrated an increased risk for lung cancer in those exposed to benzene (34). Benzene is a multipotent carcinogen in laboratory animals, inducing a variety of types of tumors, including lung tumors (32,33).
We also found elevated levels of HPMA and HBMA, biomarkers of uptake of acrolein and its homologue crotonaldehyde, respectively. Both acrolein and crotonaldehyde are weak carcinogens, and neither is known to target the lung (22,35). However, acrolein is cilia-toxic and thus may impede the clearance of toxicants and other foreign substances from the lung (36). Acrolein is highly reactive with proteins and may be involved in inflammation (37,38). Both acrolein and crotonaldehyde are products of oxidative damage and both are known to react with DNA, producing adducts, some of which have miscoding properties (3942). These adducts have been detected in various in vitro systems and in the human lung (41,43,44). There is a background level of acrolein and crotonaldehyde-DNA adducts in humans, which may be related to oxidative damage and lipid peroxidation (41,43,44). Our results suggest that such damage may be exacerbated by exposure to fumes from wok cooking, and this should be examined in future studies. Acrolein-DNA adducts have also been associated with mutations in the p53 tumor suppressor gene, as seen in lung cancer (45). Collectively, these results suggest that the increased exposure to acrolein and crotonaldehyde observed here may play some role in lung cancer induction associated with wok cooking.
The increases in levels of mercapturic acids of benzene, acrolein, and crotonaldehyde observed in this study were not nearly as great as seen in smokers (25). In a recent study, we found that levels of these mercapturic acids decreased by 7–8 fold three days after smokers stopped smoking to levels that were generally consistent with those observed in the non-smoking women in our study (25). Cigarette smoking provides a far greater exposure to these compounds than does wok cooking, so the smaller increases seen in this study are fully plausible (14,25). The high biomarker levels seen in smokers is consistent with the known amounts of benzene, acrolein, and crotonaldehyde in cigarette smoke, and with the far higher risk for lung cancer from smoking compared to indoor fume exposure.
We did not observe increases in biomarkers of exposure to 1,3-butadiene or PAH. Levels of 1,3-butadiene in fumes from heated oils are far lower than those of a number of other volatile compounds such as acrolein (14). Therefore, this result is not unexpected. While PAH have been identified in cooking oil fumes(12), they are high molecular weight, non-volatile compounds. Thus, their uptake under normal cooking circumstances would be less likely than that of the more volatile compounds such as benzene, acrolein, and crotonaldehyde
Leukocyte N2-ethylidene-dG is a biomarker of acetaldehyde exposure which is moderately increased by both cigarette smoking and alcohol consumption (29,46). However, all subjects analyzed to date have appreciable levels of this biomarker, even if they do not smoke or drink, because there are multiple sources of acetaldehyde exposure. The average levels of N2-ethylidene-dG observed here were considerably higher than in our previous studies (29,46), which may have diminished our ability to detect a change in this biomarker due to exposure to acetaldehyde, a known constituent of cooking fumes. The basis for the high DNA adduct levels observed here requires further investigation. One possibility is exposure from vegetation fires in Indonesia, which may release volatiles which were carried to Singapore by prevailing winds.
One curious finding was the lower level of HEMA, a biomarker of ethylene oxide exposure, in the women who cooked than in controls. Ethylene oxide has been identified as a constituent of cooking fumes (15). However, it could also be formed endogenously by oxidation of ethylene (47). The endogenous formation of ethylene oxide could lead to considerable variation in HEMA levels in a relatively small study such as ours. Further studies are required to investigate this finding.
One previous study carried out in Chinese restaurant workers examined the effects on biomarkers of exposure to cooking oil fumes (16). Pan et al found that urinary levels of 1-HOP and 8-hydroxy-dG, a biomarker of oxidative damage, were significantly higher in kitchen staff than in service staff. They concluded that oxidative DNA damage was associated with exposure of Chinese restaurant workers to cooking oil fumes and also observed that the response was greater in female than in male restaurant workers.
There are some limitations to this study. First, the size was quite small, with only 42–54 exposed subjects and 50 general population controls. Second, we do not have information on the cooking habits of the general population controls. Third, we do not know the exact half-lives of the biomarkers studied. Therefore a spot urine collected at randomly timed points would not be optimal for the assessment of biomarkers with short half-lives. In spite of these limitations, we observed significant differences in three carcinogen and toxicant biomarkers, which supports the hypothesis that exposure to cooking fumes is a cause of lung cancer in Chinese women.
In summary, the results of this study demonstrate elevated levels of volatile organic compound biomarkers in Chinese women who regularly cook at home. These biomarkers reflect increased exposure to volatile carcinogens and toxicants such as benzene, acrolein, and crotonaldehyde. While larger studies are needed to confirm these results, the present data, together with multiple epidemiologic studies, demonstrate the urgent need for preventive measures such as improved ventilation to efficiently remove cooking oil fumes.
ACKNOWLEDGEMENTS
We thank Ms. Siew-Hong Low of the National University of Singapore for supervising the field work of the Singapore Chinese Health Study.
Grant support: This study was supported by grants ES-11297 from the National Institute of Environmental Health Sciences and CA-80205 from the National Cancer Institute. Mass spectrometry was carried out in the core facilities of the Masonic Cancer Center, University of Minnesota, supported in part by National Cancer Institute grant CA-77598.
1. Cancer Incidence in Five Continents. Vol. IX. Lyon, FR: IARC; 2007.
2. American Cancer Society. Global Cancer Facts and Figures 2007. Atlanta: American Cancer Society; 2007. pp. 14–16.
3. Yu IT, Chiu YL, Au JS, Wong TW, Tang JL. Dose-response relationship between cooking fumes exposures and lung cancer among Chinese nonsmoking women. Cancer Res. 2006;66:4961–4967. [PubMed]
4. Straif K, Baan R, Grosse Y, Secretan B, El Ghissassi F, Cogliano V. Carcinogenicity of household solid fuel combustion and of high-temperature frying. Lancet Oncol. 2006;7:977–978. [PubMed]
5. Gao YT, Zheng W, Ershow AG, et al. Lung cancer among chinese women. Int J Cancer. 1987;40:604–609. [PubMed]
6. Ko YC, Lee CH, Chen MJ, et al. Risk factors for primary lung cancer among non-smoking women in Taiwan. Int J Epidemiol. 1997;26:24–31. [PubMed]
7. Zhong L, Goldberg MS, Gao YT, Jin F. Lung cancer and indoor air pollution arising from Chinese-style cooking among nonsmoking women living in Shanghai, China. Epidemiology. 1999;10:488–494. [PubMed]
8. Seow A, Poh WT, Teh M, et al. Fumes from meat cooking and lung cancer risk in Chinese women. Cancer Epidemiol Biomarkers Prev. 2000;9:1215–1221. [PubMed]
9. Metayer C, Wang Z, Kleinerman RA, et al. Cooking oil fumes and risk of lung cancer in women in rural Gansu, China. Lung Cancer. 2002;35:111–117. [PubMed]
10. Wang XR, Chiu YL, Qiu H, Au JS, Yu IT. The roles of smoking and cooking emissions in lung cancer risk among Chinese women in Hong Kong. Ann Oncol. 2009;20:746–751. [PubMed]
11. Li M, Yin Z, Guan P, et al. XRCC1 polymorphisms, cooking oil fume and lung cancer in Chinese women nonsmokers. Lung Cancer. 2008;62:145–151. [PubMed]
12. Li S, Pan D, Wang G. Analysis of polycyclic aromatic hydrocarbons in cooking oil fumes. Arch Environ Health. 1994;49:119–122. [PubMed]
13. Shields PG, Xu GX, Blot WJ, et al. Mutagens from heated Chinese and U.S. cooking oils. J Natl Cancer Inst. 1995;87:836–841. [PubMed]
14. Pellizzari ED, Michael LC, Thomas KW, Shields PG, Harris C. Identification of 1,3-butadiene, benzene, and other volatile organics from wok oil emissions. J Expo Anal Environ Epidemiol. 1995;5:77–87. [PubMed]
15. Lin JS, Chuang KT, Huang MS, Wei KM. Emission of ethylene oxide during frying of foods in soybean oil. Food Chem Toxicol. 2007;45:568–574. [PubMed]
16. Pan CH, Chan CC, Wu KY. Effects on Chinese restaurant workers of exposure to cooking oil fumes: a cautionary note on urinary 8-hydroxy-2'-deoxyguanosine. Cancer Epidemiol Biomarkers Prev. 2008;17:3351–3357. [PubMed]
17. International Agency for Research on Cancer. IARC Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Humans. vol. 60. Lyon, FR: IARC; 1994. Some Industrial Chemicals; pp. 73–159.
18. International Agency for Research on Cancer. IARC Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Humans. vol. 29. Lyon, FR: IARC; 1982. Some Industrial Chemicals and Dyestuffs; pp. 93–148.
19. Straif K, Baan R, Grosse Y, Secretan B, El Ghissassi F, Cogliano V. Carcinogenicity of polycyclic aromatic hydrocarbons. Lancet Oncol. 2005;6:931–932. [PubMed]
20. International Agency for Research on Cancer. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans. vol. 71. Lyon, FR: IARC; 1999. Re-evaluation of Some Organic Chemicals, Hydrazine and Hydrogen Peroxide (part two) pp. 319–336. [PubMed]
21. International Agency for Research on Cancer. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans. vol. 97. Lyon, FR: IARC; 2008. 1,3-Butadiene, Ethylene Oxide and Vinyl Halides (Vinyl Fluoride, Vinyl Chloride and Vinyl Bromide) pp. 45–309. [PubMed]
22. International Agency for Research on Cancer. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans. vol. 63. Lyon, FR: IARC; 1995. Acrolein; pp. 337–391.
23. Salmon CP, Knize MG, Felton JS, Zhao B, Seow A. Heterocyclic aromatic amines in domestically prepared chicken and fish from Singapore Chinese households. Food Chem Toxicol. 2006;44:484–492. [PubMed]
24. Hankin JH, Stram DO, Arakawa K, et al. Singapore Chinese Health Study: development, validation, and calibration of the quantitative food frequency questionnaire. Nutr Cancer. 2001;39:187–195. [PubMed]
25. Carmella SG, Chen M, Han S, et al. Effects of smoking cessation on eight urinary tobacco carcinogen and toxicant biomarkers. Chem Res Toxicol. 2009;22:734–741. [PMC free article] [PubMed]
26. Carmella SG, Le K, Hecht SS. Improved method for determination of 1-hydroxypyrene in human urine. Cancer Epidemiol Biomarkers & Prev. 2004;13:1261–1264. [PubMed]
27. Hecht SS, Chen M, Yagi H, Jerina DM, Carmella SG. r-1,t-2,3,c-4-Tetrahydroxy-1,2,3,4-tetrahydrophenanthrene in human urine: a potential biomarker for assessing polycyclic aromatic hydrocarbon metabolic activation. Cancer Epidemiol Biomarkers & Prev. 2003;12:1501–1508. [PubMed]
28. Hecht SS, Chen M, Yoder A, et al. Longitudinal study of urinary phenanthrene metabolite ratios: effect of smoking on the diol epoxide pathway. Cancer Epidemiol Biomarkers & Prev. 2005;14:2969–2974. [PubMed]
29. Chen L, Wang M, Villalta PW, et al. Quantitation of an acetaldehyde adduct in human leukocyte DNA and the effect of smoking cessation. Chem Res Toxicol. 2007;20:108–113. [PMC free article] [PubMed]
30. Winer BJ. Statistical principles in experimental design. 2nd ed. New York: Mcgraw-Hill; 1971.
31. Breslow NE, Day NE. Statistical methods in cancer research. vol. 1. Lyon, France: IARC Scientific Publications; 1980. [PubMed]
32. U.S.Department of Health and Human Services. 11th Edition. N.C.: Research Triangle Park; 2004. Report on Carcinogens. pp. III-26–III-28.
33. International Agency for Research on Cancer. Overall Evaluations of Carcinogenicity: An Updating of IARC Monographs. Supplement 7. Volumes 1–42. Lyon, FR: IARC; 1987. pp. 120–122. [PubMed]
34. Hayes RB, Yin SN, Dosemeci M, et al. Mortality among benzene-exposed workers in China. Environ Health Perspect. 1996;104(Suppl 6):1349–1352. [PMC free article] [PubMed]
35. International Agency for Research on Cancer. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans. vol. 63. Lyon, France: IARC; 1995. Dry Cleaning, Some Chlorinated Solvents and Other Industrial Chemicals; pp. 373–391. [PubMed]
36. Kensler CJ, Battista SP. Components of cigarette smoke with ciliary-depressant activity. Their selective removal by filters containing activated charcoal granules. N Engl J Med. 1963;269:1161–1166. [PubMed]
37. Thompson CA, Burcham PC. Genome-wide transcriptional responses to acrolein. Chem Res Toxicol. 2008;21:2245–2256. [PubMed]
38. Kim V, Rogers TJ, Criner GJ. Frontiers in emphysema research. Semin Thorac Cardiovasc Surg. 2007;19:135–141. [PubMed]
39. Chung FL, Hecht SS. Formation of cyclic 1,N2-adducts by reaction of deoxyguanosine with α-acetoxy-N-nitrosopyrrolidine, 4-(carbethoxynitrosamino)butanal, or crotonaldehyde. Cancer Res. 1983;43:1230–1235. [PubMed]
40. Chung FL, Young R, Hecht SS. Formation of cyclic 1,N2-propanodeoxyguanosine adducts in DNA upon reaction with acrolein or crotonaldehyde. Cancer Res. 1984;44:990–995. [PubMed]
41. Chung FL, Nath RG, Nagao M, Nishikawa A, Zhou GD, Randerath K. Endogenous formation and significance of 1,N2-propanodeoxyguanosine adducts. Mutat Res -Fund Mol M. 1999;424:71–81. [PubMed]
42. Stein S, Lao Y, Yang I-Y, Hecht SS, Moriya M. Genotoxicity of acetaldehyde- and crotonaldehyde-induced 1,N2-propanodeoxyguanosine DNA adducts in human cells. Mutation Res. 2006;608:1–7. [PubMed]
43. Zhang S, Villalta PW, Wang M, Hecht SS. Analysis of crotonaldehyde- and acetaldehyde-derived 1,N2-propanodeoxyguanosine adducts in DNA from human tissues using liquid chromatography-electrsopray ionization-tandem mass spectrometry. Chem Res Toxicol. 2006;19:1386–1392. [PMC free article] [PubMed]
44. Zhang S, Villalta PW, Wang M, Hecht SS. Detection and quantitation of acrolein-derived 1,N2-propanodeoxyguanosine adducts in human lung by liquid chromatography-electrospray ionization-tandem mass spectrometry. Chem Res Toxicol. 2007;20:565–571. [PMC free article] [PubMed]
45. Feng Z, Hu W, Hu Y, Tang M-S. Acrolein is a major cigarette-related lung cancer agent. Preferential binding at p53 mutational hotspots and inhibition of DNA repair. Proc Natl Acad Sci USA. 2006;103:15404–15409. [PubMed]
46. Balbo S, Hashibe M, Gundy S, et al. N2-ethyldeoxyguanosine as a potential biomarker for assessing effects of alcohol consumption on DNA. Cancer Epidemiol Biomarkers Prev. 2008;17:3026–3032. [PubMed]
47. U.S.Department of Health and Human Services. Report on Carcinogens. 11th Edition. N.C.: Research Triangle Park; 2004. pp. III-118–III-122.