A case-referent study of lung cancer and incense smoke, smoking, and residential radon in chinese men.
BACKGROUND: Burning incense generates large amounts of air pollutants, many of which are confirmed or suspected human lung The human lungs are the human organs of respiration.
Humans have two lungs, with the left being divided into two lobes and the right into three lobes. Together, the lungs contain approximately 1500 miles (2,400 km) of airways and 300 to 500 million alveoli, having a total carcinogens.
OBJECTIVES: We conducted a population-based case-referent study to examine the effect of incense smoke exposure on lung cancer lung cancer, cancer that originates in the tissues of the lungs. Lung cancer is the leading cause of cancer death in the United States in both men and women. Like other cancers, lung cancer occurs after repeated insults to the genetic material of the cell. risk among Chinese males and explored the joint effect of cigarette smoking and exposure to residential radon.
METHODS: We recruited 1,208 male lung cancer incident cases and 1,069 community referents from 2004 to 2006 and estimated their lifetime exposures to incense smoke and other residential indoor air pollutants based on self-reported information collected during interviews. We performed unconditional multivariable logistic regression In statistics, logistic regression is a regression model for binomially distributed response/dependent variables. It is useful for modeling the probability of an event occurring as a function of other factors. analysis to estimate the odds ratio (OR) for lung cancer associated with exposure to incense smoke after adjusting for possible confounders. We conducted stratified stratified /strat·i·fied/ (strat´i-fid) formed or arranged in layers.
Arranged in the form of layers or strata. analyses by smoking status and exposures to incense burning and residential radon and explored the potential additive-scale interactions.
RESULTS: We observed an association between incense exposure and lung cancer that was limited primarily to smokers. Cigarette smoking and high cumulative incense exposure at home appeared to have a synergistic effect Synergistic effect
A violation of value-additivity in that the value of a combination is greater than the sum of the individual values. on lung cancer (compared with never-smokers who never used incense, the OR for Jung cancer for smokers who used incense [greater than or equal to] 60 day-years = 5.00; 95% confidence interval confidence interval,
n a statistical device used to determine the range within which an acceptable datum would fall. Confidence intervals are usually expressed in percentages, typically 95% or 99%. ; 3.34, 7.51). Power was limited, but we also found preliminary evidence suggesting that radon exposure may increase risk among smokers using incense.
CONCLUSION: Our study suggests that exposure to incense smoke in the home may increase the risk of lung cancer among smokers and that exposure to radon may further increase risk.
KEY WORDS: incense burning, lung neoplasm neoplasm or tumor, tissue composed of cells that grow in an abnormal way. Normal tissue is growth-limited, i.e., cell reproduction is equal to cell death. , residential radon, smoking. Environ Health Perspect 119:1641-1646 (2011). http://dx.doi.org/10.1289/ehp.1002790 [Online22July2011]
Indoor air pollution resulting from burning incense is a major public health problem in Hong Kong Hong Kong (hŏng kŏng), Mandarin Xianggang, special administrative region of China, formerly a British crown colony (2005 est. pop. 6,899,000), land area 422 sq mi (1,092 sq km), adjacent to Guangdong prov. and other Asian countries, where burning incense to worship gods and ancestors is a popular ritual with a long traditional practice (Ho and Yu 2002; Lung et al. 2003). A previous survey showed that about half of Chinese families in Hong Kong burned incense at home, usually mice a day (Koo and Ho 1996). Burning incense generates large amounts of particulate matter particulate matter
n. Abbr. PM
Material suspended in the air in the form of minute solid particles or liquid droplets, especially when considered as an atmospheric pollutant.
Noun 1. (PM), aerosols, nitrogen dioxide nitrogen dioxide
A poisonous brown gas, NO2, often found in smog and automobile exhaust fumes and synthesized for use as a nitrating agent, a catalyst, and an oxidizing agent.
Noun 1. , sulfur dioxide sulfur dioxide, chemical compound, SO2, a colorless gas with a pungent, suffocating odor. It is readily soluble in cold water, sparingly soluble in hot water, and soluble in alcohol, acetic acid, and sulfuric acid. , formaldehyde formaldehyde (fôrmăl`dəhīd'), HCHO, the simplest aldehyde. It melts at −92°C;, boils at −21°C;, and is soluble in water, alcohol, and ether; at STP, it is a flammable, poisonous, colorless gas with a suffocating , benzene benzene (bĕn`zēn, bĕnzēn`), colorless, flammable, toxic liquid with a pleasant aromatic odor. It boils at 80.1°C; and solidifies at 5.5°C;. Benzene is a hydrocarbon, with formula C6H6. , polycyclic polycyclic
having two or more usually fused chemical ring structures in their molecule.
thyroid initiators, i.e. they increase the incidence of thyroid tumors. aromatic hydrocarbons (PAHs), and other volatile organic compounds (Lin et al. 2008; Lu et al. 2008; Wang et al. 2007); many of these are confirmed or suspected human carcinogens associated with lung cancer [International Agency for Research on Cancer The International Agency for Research on Cancer (IARC, or CIRC in its French acronym) is an intergovernmental agency forming part of the World Health Organisation of the United Nations.
Its main offices are in Lyon, France. (IARC) 2010a, 2010b; Lin et al. 2008J. However, rhe association between burning incense and lung cancer is uncertain, and epidemiological evidence is very limited.
Previous studies of incense smoke exposure and lung cancer, which were based mainly on females, have not demonstrated a consistent association (Chan-Yeung et al. 2003; Chen et al. 1990; Ger et al. 1993; Koo and Ho 1996; MacLennan et al. 1977). Because incense smoke condensates contain hazardous agents similar to those found in tobacco smoke, including many that were mutagenic mutagenic
inducing genetic mutation. and genotoxic genotoxic /ge·no·tox·ic/ (je´no-tok?sik) damaging to DNA: pertaining to agents known to damage DNA, thereby causing mutations, which can result in cancer.
adj. in the Ames test Ames test
A test in which strains of Salmonella that are unable to synthesize histidine are introduced into a test substance lacking in histidine. (Chen and Lee 1996), it is logical to hypothesize hy·poth·e·size
v. hy·poth·e·sized, hy·poth·e·siz·ing, hy·poth·e·siz·es
To assert as a hypothesis.
To form a hypothesis. that exposure to incense smoke could also increase lung cancer risk. On the other hand, carcinogenic carcinogenic
having a capacity for carcinogenesis. exposures may be much less intensive than those associated with active cigarette smoking, and an independent effect of incense burning on lung cancer might not be discernable in the general population.
Using data from a Luge luge (lzh), a type of small sled on which one or two persons, lying face up, slide feet first down snowy hillsides or down steeply banked, curving, iced chutes similar to those used in population-based case-referent study conducted among Chinese males, we examined the association between incense smoke exposure and lung cancer, stratified by smoking status. We further explored the possible joint effect of incense smoke and exposure to residential radon.
Materials and Methods
Study design and the subjects. The study design of this population-based case-referent study has been described previously, where an exposure-response relation between secondhand smoke (SHS SHS Shares (stock)
SHS SAW (Surface Acoustic Wave) Humidity Sensor
SHS Sciences Humaines et Sociales (French: Social Sciences)
SHS Student Health Service
SHS Second Hand Smoke ) exposure and adenocarcinoma adenocarcinoma: see neoplasm. of the lung among never-smokers was observed (Tse ct al. 2009). In brief, we consecutively interviewed 1,208 Chinese males 35-79 years of age with incident cases otptknazy histologically his·tol·o·gy
n. pl. his·tol·o·gies
1. The anatomical study of the microscopic structure of animal and plant tissues.
2. The microscopic structure of tissue. confirmed lung cancer from 1 February 2004 to 30 September 2006 at the largest oncology center in Hong Kong; the response rate was 96%. A study questionnaire about work, lifestyle, and health among Hong Kong males that was developed by the authors was completed by 1 > 148 cases (95%) and by 60 proxy respondents for those patients who were too ill to speak. Of the proxies, 90% were the wives of the patients (the other 10% were other household members), and the information they provided was subsequently confirmed by the patients. We further interviewed 1,069 male referents that were randomly selected from residential telephone directories for the same districts in which the cases resided, with a response rate of 48%. Each community referent was frequency matched to cases in 5-year age groups and had no history of physician-diagnosed cancer in any site. This study was approved by the ethics committees of both the Chinese University of Hong Kong The motto of the university is "博文約禮" in Chinese, meaning "to broaden one's intellectual horizon and keep within the bounds of propriety". and Queen Elizabeth Hospital Queen Elizabeth Hospital can refer to one of several hospitals named after either Elizabeth II of the United Kingdom or Queen Elizabeth the Queen Mother:
Date conection. personal interviews were carried out by trained interviewers to collect information on each subject, including demographic data, habits of tobacco smoking and alcohol drinking, dietary habits, cancer history in first-degree relatives, living density, ventilation and sources of indoor air pollution in the residence, and exposures to confirmed or suspected occupational carcinogens. Relevant medical information including medical diagnosis and histology histology (hĭstŏl`əjē), study of the groups of specialized cells called tissues that are found in most multicellular plants and animals. was retrieved from the hospital records. Men were classified as ever-smokers if they had smoked > 20 packs of cigarettes or 12 oz of tobacco in their lifetime or smoked > 1 cigarette/day or > 1 cigar/week tor 1 year (Ferris 1978). Exposure to confirmed or suspected occupational carcinogens was defined as ever regularly exposed (i.e., at (east once a week for at least 6 months) to any of these agents: silica, asbestos, arsenic, nickel, chromium, tars, asphalts, painting, pesticide, diesel, cooking fume fume Occupational medicine A solid suspension resulting from condensation of the products of combustion. See Inhalant Vox populi verbTo be in the midst of a mental mini-meltdown. , and welding fume in the workplace (Tse et al. 2009).
Assessment of indoor air pollutants. We collected information on lifetime exposure to various indoor air pollutants in the home for each participant since childhood, including incense burning, residential radon exposure, SHS, years of cooking by frying, type of fuel use, and exposure to mosquito coil burning inside the house during summer months (never and ever).
Questions on SHS exposure in the home included "Did any person (including parents, spouse, children, or any other relatives or friends) who had been living with you (since your childhood) smoke any tobacco product regularly in your presence at home? If so, what is the relationship between you and the smoker, and how long has he (or she) smoked?" We also collected information on SHS exposure of participants from each workplace by asking the question "Did any person who had been working with you smoke any tobacco product regularly in your presence?" SHS exposure was defined as ever lived or worked with a smoker for at least 1 year and was regularly exposed to tobacco smoke (Tse etal. 2009; Yu et al. 2006a).
We collected information on incense smoke exposure at home using these questions: "Did any person including yourself burn any incense products (e.g., joss sticks, scented coil) inside your home? If yes, how often did such person burn incense products inside the room (i.e., the frequency: times a day, times a week, times a month), and how many years has such habit been maintained?" Ever exposure to incense smoke referred to inhalation of incense smoke at least once per month for a year or more. Lifetime cumulative exposure to incense smoke in the home was the product of frequency of exposure to incense smoke per day by years of exposure. Cumulative residential radon exposure was assessed semiquantitatively based on detailed information about all residences during their lifetime, including building age, floor level, window-opening practices, building materials Building materials used in the construction industry to create .
These categories of materials and products are used by and construction project managers to specify the materials and methods used for . , and wall surface-covering materials according to according to
1. As stated or indicated by; on the authority of: according to historians.
2. In keeping with: according to instructions.
3. an established formula recommended by Hong Kong Government (Lee 1997). This formula was derived from a territory-wide indoor radon survey in Hong Kone, as described in detail by Yu et al. (2006a) in their Appendix A. The score of cumulative residential radon exposure does not have a unit, and a higher score indicates a higher level of exposure to residential radon.
Statistical analysis. Chisquare tests or Mests were used to examine differences of incense smoke exposure and other selected risk factors between the cases and referents. We used the median of exposed community referents as the cut point to classify low and high exposure levels for the frequency of incense burning (1-2 times/day and > 2 times/day) and cumulative exposure (1-60 day-years and > 60 day-years, where 2 day-years is equivalent to burning incense twice a day for 1 year, or once a day for 2 years, etc.), respectively, whereas those never exposed to incense burning were treated separately as the reference group. Cumulative residential radon exposure was classified according to the first, second, third, and fourth quartiles (< 7.78, 7.78 to < 8.86, > 8.86 to < 9.62, > 9.62, respectively), based on the distribution of exposure scores in referents, and to low (score < 8.86) and high (score > 8.86) levels, based on the median score in referents. A radon-missing category was created, and it was adjusted for in the model. We fitted unconditional multivariable logistic regression models to estimate the odds ratio (OR) and the 95% confidence interval (CI) for each index of incense exposure. To select covariates for a base model, we used a forward stepwise stepwise
incremental; additional information is added at each step.
stepwise multiple regression
used when a large number of possible explanatory variables are available and there is difficulty interpreting the partial regression method to identify potential confounding factors associated with lung cancer with [RHO Rho
The rate at which the price of a derivative changes relative to a change in the risk-free rate of interest. Rho measures the sensitivity of an option or options portfolio to a change in interest rate. ] < 0.05, specifically, age, place of birth, education level, any cancer in first-degree relatives, intake of meat, alcohol consumption, and smoking pack-years. We also included SHS in the base model, although it was not a significant predictor of lung cancer. We removed smoking pack-years from the base model when the analysis was restricted to the never-smokers, and we added years of smoking cessation smoking cessation Public health Temporary or permanent halting of habitual cigarette smoking; withdrawal therapies–eg, hypnosis, psychotherapy, group counseling, exposing smokers to Pts with terminal lung CA and nicotine chewing gum are often ineffective. to the base model when analyses were restricted to ever-smokers.
We formally assessed multiplicative-scale interaction (sometimes referred to as OR modification) between smoking and incense exposure by performing likelihood ratio tests comparing models with and without a product term between smoking (ever, never) and incense exposure (any, none). We evaluated additive-scale interactions (sometimes referred to as risk difference modification) of incense exposure and smoking on lung cancer using the synergy index (SI) (Greenland and Rothman 1998), as follows:
SI = (O [R.sub.21])/[( O [R.sub.20] - 1) + (O [R.sub.01] - 1)] 
where O [R.sub.21] compares lung cancer in high incense users ([greater than or equal to] 2 times/day or [greater than or equal to] 60 day-years) who smoked with lung cancer in never-users who were never-smokers, O [R.sub.20] compares high incense users who were never-smokers with never-users who were never-smokers, and O [R.sub.01] compares never-users who smoked with the same jointly unexposed referent group. Note that subtracting 1 from each OR provides an estimate of the excess relative risk of lung cancer in each group above that in the common referent group of nonusers who were never-smokers (where O [R.sub.00] = 1). In addition, because incense use was classified into three categories (high, low, and never use), we calculated a second SI comparing joint effects of low incense use and smoking (based on O [R.sub.11], O [R.sub.10], and O [R.sub.01] for low use and smoking, low use and never-smokers, and never use and smoking compared with never use and never-smokers). We used a bootstrapping Bootstrapping
A procedure used to calculate the zero coupon yield curve from market figures.
Since the T-bills offered by the government are not available for every time period, the bootstrapping method is used to fill in the missing figures in order to derive the method (Knol et ai. 2007) to estimate 95% CIs for the SI and considered additive-scale interactions to be present if the 95% CI excluded one (Yu and Tse 2006b). The same approach was applied to examine additive-scale interactions between incense exposure and residential radon among smokers. We explored exposure-response relationships with gradients of exposure to incense smoke (i.e., as an ordinal (mathematics) ordinal - An isomorphism class of well-ordered sets. categorical variable coded using integer values of 0, 1, 2) by trend tests at an alpha level of 0.05.
The average age of cases and referents at interview was 66 years (Table 1). More lung cancer cases than referents were smokers and had smoked heavily ([greater than or equal to] 20 pack-years). Compared with referents, cases were more likely to have exposures to SHS and higher living density (fewer square meters per head), and were exposed to higher levels (more cases in the category of the fourth quartile Quartile
A statistical term describing a division of observations into four defined intervals based upon the values of the data and how they compare to the entire set of observations.
Each quartile contains 25% of the total observations. ) of radon in their residences. Less than half of the cases and referents had ever cooked at home, and gas was the most frequently used fuel in both groups. Except for cigarette smoking and exposures to SHS and residential radon, no significant differences were observed between the cases and referents in other characteristics (Table 1).
Table 1. Selected characteristics of 1,208 lung cancer cases and 1,069 community referents among Hong Kong Chinese men, 2004-2006. (a) Characteristic Referents Cases [n (%)] rho-Value [n (%)] Age at interview (b) 66.2 [+ or 65.8 + 9.5 0.326 -] 9.9 Amount of cigarette 17.1 [+ or 44.1 [+ or < smoking (pack-years) -]29.0 -]33.8 0.001 (b) Never 536 (51.7) 132 (11.1) > 0.001 <20 172 (16.6) 122 (10.2) [greater than 329 (31.7) 940 (78.7) or equal to] 20 Missing 32 14 Exposed to environmenttal tobacco smoke Never 281 (26.3) 230 (19.1) < 0.001 Ever 788 (73.7) 977 (80.9) Missing 0 1 Residential radon exposure (in quartiles) (c) First 263 (25.0) 230 (20.3) 0.002 Second 261 (24.8) 302 (26.6) Third 267 (25.2) 255 (22.4) Fourth 263 (25.0) 349 (30.7) Missing 15 72 Exposed to mosquito coil burning Never 967 (90.5) 1066 (88.2) 0,088 Ever 102 (9.5) 142 (11.8) Living density 9.66 [+ or 8.97 [+ or -] 0.068 (square meters per -]10 7.54 head) (b) Residential ventilation Poor 530 (49.6) 616 (51.0) 0.501 Good 539 (50.4) 592 (49.0) Cook at home Never 587 (55.8) 699 (58.4) 0.214 Ever 465 (44.2) 498 (41.6) Missing 17 11 Separate room for cooking at home Never 629 (58.9) 743 (61.6) 0.350 Not always 216 (20.2) 237 (19.7) Always 223 (20.9) 226 (18.7) Missing 1 2 Use exhaust appliances for cooking at home Never 667 (63.0) 791 (66.2) 0.272 Not always 193 (18.2) 195 (16.3) Always 199 (18.8) 209 (17.5) Missing 10 13 Types of fuel use Never and/or 604 (57.5) 706 (59.0) 0.459 electricity Gas only 359 (34.2) 376 (31.4) Liquid and/or gas 63 (6.0) 85 (7.1) Solid and/or gas 25 (2.3) 30 (2.5) Missing 18 11 Histology Squamous cell 272 (22.5) carcinoma Adenocarcinoma 440 (36.4) Small-cell carcinoma 118 (9.8) Large-cell carcinoma 25 (2.1) Other or not 353 (29.2) otherwise specified (a) Observations with missing data were not included when calculating the percentage. (b) Mean + SD. (c) Using the quartile score of community referents as the cut point (first, second, third, and fourth quartile: (< 7.78, 7.78 to < 8.86, > 8.86 to < 9.62, and > 9.62, respectively) to classify different levels of radon exposure.
The variable with the highest proportion of missing data was radon (72 cases and 15 referents). There were no missing data for smoking status, and few observations with missing data for incense burning (four cases) and SHS (one case) exposure. Data from 1,109 lung cancer cases and 1,015 referents with complete information were included in the analyses. Generally, there were no significant differences in major characteristics (e.g., education, place of birth, alcohol drinking and smoking habits, family cancer history, and meat intakes) between cases or referents with missing data and those included in the analysis, with the exception of age. The referents with missing data were 4.4 years younger, on average, than were referents included in the analyses (data not shown). We examined the correlations among cigarette smoking, incense exposure, and residential radon exposure and found low correlations (correlation coefficients ranged from -0.007 to 0.105) between chem.
More cases than referents ever had exposures to incense smoke at home (around 65% and 55%, respectively) (Table 2). The mean [+ or -] SD of the duration of exposure to incense burning was 50.3 [+ or -] 22.4 years for lung cancer cases and 49.1 [+ or -] 21.4 years for the referents; this finding indicates that burning incense was a long-term practice in the homes for most Hong Kong Chinese. In the population as a whole, lung cancer risk was significantly increased among men exposed to frequent incense burning ([greater than or equal to] 2 times/day; OR = 1.26; 95% CI: 1.01, 1.58) and high cumulative incense exposure ([greater than or equal to] 60 day-years; OR = 1.38; 95% CI: 1.10, 1.75) compared with men who were never exposed to incense (Table 2). Jncense use did nor appear to be associated with lung cancer among never-smokers (e.g., OR = 0.95; 95% CI: 0.59, 1.53 for frequent use vs. never use), but there was some indication that frequent use and high cumulative use (vs. never use) was associated with lung cancer among smokers (trend test ^-values of high 0.039 and 0.007, respectively.) In addition, the synergy index for smoking and frequent incense use' (SI = 1.50; 95% CI: 0.98, 2.51) or cumulative exposure and cigarette smoking (SI = 1.59; 95% CI; 1.06, 2.62) indicated that the joint effect of these two exposures was > 50% than expected assuming additive effects on lung cancer risk. The synergy index for smoking and low level of incense exposure (i.e., < 2 times/day or < 60 day-years) was close to L0, and there was no statistical significance.
Table 2. Associations between lung cancer risk and exposures to incense burning in the homes of Hong Kong Chinese men, 2004-2006. (a) (b) All subjects Synergy index Referents Cases (C) (n= (n OR (95% 1,069) =1,208) CI) n (%) n (%) Frequency of incense burning (times/day) Never 479 420 1.00 (44.8) (34.8) <2 248 313(25.9) 1.16(0.90,1.48) (23.2) [greater 342 471 1.26(1.01,1.58) than or (32.0) (39.0) equal to]2 p-Value 0.044 (test for trend) 1.50(0.98, 2.51 ) (d) Cumulative incense exposure (day-years) Never 479 420 1.00 (44.8) (34.8) <60 280 337 1.05(0.82,1.34) (26.2) (27.9) [greater 310(29.0) 448(37.1) 1.38(1.10,1.75) than or equal to]60 p-Value 0.007 (test for trend) 1.59(1.06,2.62) (e) Never-smokers Synergy Referents Cases index (n = 536) (n=132) OR (95% (C) n(%) n (%) CI) Frequency of incense burning (times/day) Never 259 61 (46.2) 1.00 (48.3) <2 111(20.7) 33(25.0) 1.15(0.69,1.90) [greater 166(31.0) 38 (28.8) 0.95(0.59,1.53) than or equal to]2 p-Value 0.908 (test for trend) 1.50 0.98, 2.51) (d) Cumulative incense exposure (day-years) Never 259 61 (46.2) 1.00 (48.3) <60 123(22.9) 32 (24.2) 0.98 (0.59,1.61) [greater 154(28.7) 39 (29.5) 1.10(0.68,1.76) than or equal to]60 p-Value 0.739 (test for trend) 1.59 (1.06,2.62) (e) Ever-smokers Synergy index Referents Cases (C) (n = 533) (n= 1,076) n (%) n(%) OR (95% CI) Frequency of incense burning (times/day) Never 220(41.3) 359 (33.4) 3.38(2.29,5.01) <2 137(25.7) 280 (26.0) 3.72(2.46,5.61) [greater 176(33.0) 433 (40.2) 4.49 (3.02, 6.69)(d) than or equal to]2 p-Value 0.039 (test for trend) 1.50(0.98, 2.51) (d) Cumulative incense exposure (day-years) Never 220(41.3) 359 (33.4) 3.42(2.31,5.06) <60 157(29.5) 305 (28.3) 3.43(2.29,5.14) [greater 156(29.3) 409 (38.0) 5.00 (3.34, 7.51 than or )e equal to]60 p-Value 0.007 (test for trend) 1.59(1.06,2.62) (e)
Compared with men who never used incense and who had low radon exposure, the adjusted OR for men who used incense frequently and who had high radon exposure was 1.50 (95% CI: 1.02, 2.22; 240 cases) (Table 3), and the OR for men with high cumulative exposure and high radon was 1.58 (95% CI: 1.06, 2.36; 222 cases) (Table 4). ORs for joint exposure to high radon and frequent or high cumulative incense use were increased when incense use was classified according to quartiles (Table 3 and 4), but power was limited, and none of the synergy indices were statistically significant (data not shown).
Table 3. Associations between lung cancer and frequency of incense smoke exposure stratified by exposure status of residential radon among Chinese smoking men, 2004-2006 [OR (95% CI)]. (a), (b) Frequency of inense exposure Levels of No incense < 2 [greater than or equal to]2 radon times/day times/day exposure Residential radon (c) Low 1.00 1.10 1.09(0.72,1.66) (0./1.1.71) High 1.00(0.67,1.48) 1.06(0.68,1.65) 1.50(1.02,2.22) Residential radon exposure (d) First 1.00 0.81(0.44,1.51) 0.88(0.46,1.66) quartile Second 0.96 1.45(0.76,2.74) 1.21(0.68,2.14) quartile (0.55,1.68) Third 0.83(0.46,1.49) 1.10(0.57,2.14) 1.12(0.65,1.94) quartile Fourth 1.12(0.64,1.97) 1.01(0.55,1.84) 1.98(1.12,3.49) quartile (a) Missing data for 31 lung cancer cases and 35 community referents were not included in the analyses. (b) Variables included in the models were age, place of birth, education level, smoking pack-years, years of smoking cessation, alcohol drinking, any cancer in first-degree relatives, and intake of meat. (c) Using the median score of community referents as the cut point to classify the low (score <8.86) and high level (score [greater than or equal to] 8.86) of radon exposure. (d) Using the quartile score of community referents as the cut point (first, second, third, and fourth quartile: < 7.78, 7.78 to < 8.86, > 8.86 to < 9.62, and > 9.62, respectively) to classify different levels of radon exposure. Table 4. Associations between lung cancer and cumulative incense exposure stratified by exposure status of residential radon among Chinese smoking men, 2004-2006 [OR (95% CI)]. (a), (b) Cumulative incense exposure Levels of No incense < 60 [greater than or equal to]60 radon (day-years) (day-years) exposure Residential radon (c) Low 1.00 0.98(0.64,1.50) 1.23(0.80,1.91) High 0.99(0.67,1.48) 1.04(0.68,1.58) 1.58(1.06,2.36) Residential radon exposure (d) First 1.00 0.63(0.34,1.15) 1.27(0.64,2.52) quartile Second 0.96(0.55,1.67) 1.48(0.79,2.75) 1.17(0.65,2.09) quartile Third 0.83(0.46,1.49) 1.09(0.58,2.06) 1.14(0.65,1.99) quartile Fourth 1.12(0.64,1.95) 0.97(0.54,1.75) 2.18(1.21,3.92) quartile (a) Missing data of 31 lung cancer cases and 35 community referents were not included in the analyses. (b) Variables included in the models were age, place of birth, education level, smoking pack-years, years of smoking cessation, alcohol drinking, any cancer in first-degree relatives, and intake of meat. (c) Using the median score of community referents as the cut point to classify the low (score < 8.86) and high level (score > 8.86) of radon exposure. (d) Using the quartile score of community referents as the cut point (first, second, third, and fourth quartile: < 7,78,7.78 to < 8.86, > 8.86 to < 9.62, and > 9.62, respectively) to classify different levels of radon exposure.
Separate analyses for major histological his·tol·o·gy
n. pl. his·tol·o·gies
1. The anatomical study of the microscopic structure of animal and plant tissues.
2. The microscopic structure of tissue. types of lung cancer did not show evidence of heterogeneity among subtypes, although power to evaluate differences was limited, particularly for large-cell carcinoma (total of 25 cases).
High cumulative exposure or frequent exposure to incense smoke was significantly associated with lung cancer in Chinese men, whereas associations with lower levels of exposure were weak or absent. In addition, associations appeared to be limited to smokers, which is consistent with a synergistic interaction between cigarette smoking and high cumulative incense exposure at home on lung cancer risk. Although power was limited, our results also suggest that radon exposure might modify the association between incense use and lung cancer among men who smoked.
The earliest study on incense burning was conducted by MacLennan et al. in Singapore in the 1970s (MacLennan et al. 1977), which reported a strong relationship between incense burning and lung cancer, especially for women who burned incense while sleeping (OR = 4.11; p < 0.01) (MacLennan et al. 1977). However, their results were not confirmed in two subsequent case-referent studies in Taiwan (Chen et al. 1990; Ger et al. 1993). Chen et al. did not find an association between burning incense and adenocarcinoma (age-sex adjusted OR = 0.99; p > 0.05) but observed a slightly increased relative risk of small-cell carcinoma of the lung (age-sex adjusted OR = 1.33; p > 0.05) in a study using ophthalmic patients as referents (Chen et al. 1990). Using hospital and neighborhood referents, respectively, Ger et al. (1993) observed positive associations with adenocarcinoma among those exposed to incense burning 1-13 times/week (OR = 1.17; 95% CI; 0.34, 3.99 and OR = 1.38; 95% CI: 0.39, 4.94), but inverse associations (OR = 0.27; 95% CI: 0.13, 0.57 and OR - 0.24; 95% CI: 0.10, 0.60) with higher exposures. They also mentioned in their discussion that burning incense was positively associated with lung cancer in females (p > 0.10) but was inversely associated in males (p < 0.01). Unfortunately, no relevant data could be obtained in their main results, which prevented us from understanding the detailed relationship. Incense burning was identified as a major source of indoor air pollution in Hong Kong Air pollution in Hong Kong is considered a serious problem.
Not only the flora and fauna are affected but also humans. Cases of asthma and bronchial infections have soared in recent years, and doctors place the blame squarely on poor air quality. (Koo and Ho 1996) but was not associated with lung cancer among nonsmoking non·smok·ing
1. Not engaging in the smoking of tobacco: nonsmoking passengers.
2. Designated or reserved for nonsmokers: the nonsmoking section of a restaurant. women and was inversely associated with lung cancer in smoking women. Koo and Ho (1996) attributed the apparent protective effect in smokers to healthier diets among smoking women who burned incense compared with smoking women who did not burn incense. No data were provided to support the speculation. Our own data in the current study did not support the hypothesis of healthier diet among incense users, as smokers who burned incense at home actually had poorer diets (consumed fewer fresh vegetables and fruits, but more fried food) than those who did not use incense (data not shown). Diet would be a confounder, as a healthier diet in smokers might have explained the inverse association in the study of Koo and Ho (1996), but in our study a poorer diet among smokers may explain the positive association; the potential confounding effect of diet has been adjusted in our study. More recently (in 2003), in a hospital-based study of lung cancer using respiratory clinic patients as referents (including 46% diagnosed with asthma and 5% with chronic obstructive lung diseases), Chan-Yeung et al. (2003) observed an insignificant positive association with daily exposure to incense smoke (vs. no or < 2 years of exposure) among Hong Kong Chinese women (OR = 1.58; 95% CI: 0.77, 3.26; 71 cases) but no association among men (OR = 0.94; 95% CI: 0.56, 1.56; 100 cases) (Chan-Yeung et al. 2003). On the whole, these five previous studies have suffered from several important methodological limitations, including inappropriate choice of referents, inadequate adjustment for major confounding factors, and small study size. Thus, they have provided very limited evidence on the possible association between incense smoke exposure and lung cancer (Chan-Yeung et al. 2003; Chen et al. 1990; Ger et al. 1993; Koo and Ho 1996; MacLennan et al. 1977).
In a prospective cohort study A cohort study is a form of longitudinal study used in medicine and social science. It is one type of study design.
In medicine, it is usually undertaken to obtain evidence to try to refute the existence of a suspected association between cause and disease; failure to refute , Friborg et al. (2008) reported that long-term daily use of incense was associated with squamous cell carcinoma squamous cell carcinoma
A carcinoma that arises from squamous epithelium and is the most common form of skin cancer. Also called cancroid, epidermoid carcinoma. of the entire respiratory tract respiratory tract
The air passages from the nose to the pulmonary alveoli, including the pharynx, larynx, trachea, and bronchi.
Respiratory tract (OR = 1.8; 95% CI: 1.2, 2.6; 59 cases) (particularly in the upper part) among 61,032 Singapore Chinese of the Hokkien or Cantonese dialect Noun 1. Cantonese dialect - the dialect of Chinese spoken in Canton and neighboring provinces and in Hong Kong and elsewhere outside China
Cantonese, Yue, Yue dialect group from 1993 to 2005; however, they found no association with lung cancer overall (OR = 0.9; 95% CI; 0.7, 1.2; 93 lung cancer cases). The independent effect of indoor inhalants inhalants,
n.pl 1. chemical vapors that are inhaled for their mind-altering effects.
2. in herbology, volatile herbal compounds that are delivered by holding a soaked pad to the nose and mouth, by placing the herbs in steaming water, or including incense burning and the possible joint effect with cigarette smoking was further examined by Tang et al. (2010). By combining two hospital-based case-referent studies conducted from 1996 to 1998 and from 2005 co 2008, Tang et al. (2010) found evidence of a strong interaction between burning incense or mosquito coils and ever smoking on lung cancer risk among Singapore Chinese women, with no evidence of an association between burning incense or mosquito coils and lung cancer among never-smokers (Tang et al. 2010). The primary concern of a hospital-based case-referent study is that including referents with diseases that might also be caused by the exposure of interest will bias associations toward the null. This would be a particular concern when respiratory patients are used as referents but would be less of a concern in other cases, as is the case in the study of Tang et al. (2010) who excluded patients admitted for a diagnosis and treatment of cancer or chronic respiratory disease Noun 1. respiratory disease - a disease affecting the respiratory system
respiratory disorder, respiratory illness
adult respiratory distress syndrome, ARDS, wet lung, white lung - acute lung injury characterized by coughing and rales; inflammation of the and used a wide range of conditions, including diseases of skin, bones, joints, and connective tissue, and acute trauma as the referents; nevertheless, the generalization of the results to the general population would still be a concern. We did not observe a significant association between mosquito coil burning and lung cancer among Hong Kong Chinese men.
As proposed by Tang et al. (2010), a chronic inflammatory response in the airways induced by smoking might contribute to an interaction between cigarette smoking and incense exposure (Tang et al. 2010). Chronic inflammation chronic inflammation
Inflammation that may have a rapid or slow onset but is characterized primarily by its persistence and lack of clear resolution; it occurs when the tissues are unable to overcome the effects of the injuring agent. in the lungs may increase the interaction of hydroxyl hydroxyl /hy·drox·yl/ (hi-drok´sil) the univalent radical OH.
The univalent radical or group OH, a characteristic component of bases, certain acids, phenols, alcohols, carboxylic radicals (arising from incense smoke exposure) with DNA DNA: see nucleic acid.
or deoxyribonucleic acid
One of two types of nucleic acid (the other is RNA); a complex organic compound found in all living cells and many viruses. It is the chemical substance of genes. which in turn may increase the likelihood of mutations during the replication of DNA (Schottenfeld and Beebe-Dimmer 2010).
Radon is a confirmed human carcinogen carcinogen: see cancer.
Agent that can cause cancer. Exposure to one or more carcinogens, including certain chemicals, radiation, and certain viruses, can initiate cancer under conditions not completely understood. , and an effect on lung cancer has been established based on studies of uranium miners (IARC 1988). Radon inside buildings in Hong Kong is released mainly from concrete materials. A territory-wide indoor radon survey conducted by the Environmental Protection Department showed that radon levels of 5% of the residential buildings in Hong Kong were above the safety guideline level of the World Health Organization (WHO) of 200 Bq/m3 (Ho 2010). A pooled analysis of 13 European case-referent studies showed a synergistic interaction between radon in homes and smoking on lung cancer, with an absolute risk of lung cancer by years of age due to radon exposure among cigarette smokers estimated to be 25 times greater than the risk among lifelong never-smokers (Darby et al. 2005). In our study male smokers with the highest exposures to residential radon and incense burning were at greater risk of lung cancer than smokers with high incense exposure but low radon exposure, consistent with a synergistic effect of incense and radon, although power was limited for this analysis. Radioactive radon decay products may effectively attach to aerosols, dusts, and other particles in the air and enters our lungs with breathing (WHO 2009). Radon progeny PROGENY - 1961. Report generator for UNIVAX SS90. are then deposited on the cell lining of the airways, where the alpha particles as well as the inhaled toxic aerosols or particles (generated by burning incense or cigarettes) may interact to damage DNA, potentially causing an excess risk of lung cancer. The risk may be further enhanced among cigarette smokers because of chronic inflammatory processes.
Burning incense has been a long tradition for worship in many Chinese families, and three incense sticks are usually burnt during each prayer in their homes. Based on one study, nearly 40% of families did not open windows when worshipping (Lung et al. 2003). People exposed to incense smoke may inhale in·hale
1. To breathe in; inspire.
2. To draw something such as smoke or a medicinal mist into the lungs by breathing; inspire. a complex mixture of PM, gaseous products, and many organic compounds. A major shortcoming of the present study is the lack of direct measurements to characterize indoor inhalants. Although direct measurements were not available, some information is available from previous studies for risk assessment (Ho and Yu 2002; Lung et al. 2003; Wang et al. 2007). Ho and Yu (2002) observed a prolonged high exposure to formaldehyde (> 100 ([micro] g/[m.sup.3] for 2-3 hr) when incense was burned in the home 2-3 times a day. Lung et al. reported that PMjq concentrations near the altar during incense burning were > 9 and 1.6 times the background levels under unventilated and ventilated ven·ti·late
tr.v. ven·ti·lat·ed, ven·ti·lat·ing, ven·ti·lates
1. To admit fresh air into (a mine, for example) to replace stale or noxious air.
2. conditions, with measured concentrations of 723 and 178 [ig/m3, respectively (Lung et al. 2003). Persistently high levels of P [M.sub.10] and particulate PAHs were detected for at least 6 hr after incense was burned in an unventilated home but were substantially reduced with improved ventilation (Lung et al. 2003). A recent study reported significantly increased DNA damage and decreased DNA repair DNA repair refers to a collection of processes by which a cell identifies and corrects damage to the DNA molecules that encode its genome. In human cells, both normal metabolic activities and environmental factors such as UV light can cause DNA damage, resulting in as many as 1 capacity among temple workers with daily exposure to incense smoke compared with workers in an occupational setting unrelated to benzene, butadiene butadiene (byt'ədī`ēn), colorless, gaseous hydrocarbon. There are two structural isomers of butadiene; they differ in the location of the two carbon-carbon double bonds in the , or PAH PAH, PAHA aminohippuric acid.
PAH 1 Polycyclic aromatic hydrocarbon, see there 2. Pulmonary artery HTN exposure (Navasumrit et al. 2008), which provides supportive evidence that exposure to incense smoke may increase the risk of lung cancer.
The association between incense burning and lung cancer among women may be stronger than in men, because women in traditional Chinese families spend more time in the home. Two previous studies looked at men and women separately and found that the lung cancer risk was positively associated with burning incense for women only, although power was very limited (Chan-Yeung et al. 2003; Ger et al. 1993). We did not find an association between incense smoke exposure and lung cancer among never-smoking men but observed a) a significantly increased OR among smokers who were exposed to incense burning, and b) a slightly stronger relationship with greater cumulative incense exposure. All previous studies used the frequency of incense burning as an exposure indicator; none of them examined the association between cumulative exposure to incense smoke and lung cancer risk.
Selection bias is possible, as the cases (96%) and referents (48%) had different participant rates. We chose the community referents matched for the district of residents of the cases, which is likely to have improved comparability relative to use of referents who were not from the same districts. The prevalence of ever smoking of our community referents was 49.9%, which was very close to that of a population-based random sample of 1,506 men 26-70 years of age from the same area (54.4%) (Cheng and Ng 2007). However, data on incense burning in the general population are not available.
Recall bias is usually less of a concern for habitual exposure (which is probably what incense burning would be). Residual confounding from cigarette smoking could be a concern, but it should have been dealt with adequately by incorporating the amount and years of smoking as well as years since smoking cessation into the regression models. Given that incense burning is a traditional ritual, it seems likely that men from families who burn incense may differ from families that do not burn incense in many ways, including religious practices that might be relevant to health behaviors, ethnicity, diet, etc. Residual confounding from religious practices could not be ruled out completely, and we acknowledge it as a potential limitation of the study. People burning incense at home may be more likely to worship in temples; however, information on incense smoke exposure outside the home was not collected, which is another limitation of our study.
In conclusion, compared with men who were never exposed to incense in the home, we observed a modest excess risk of lung cancer among men who had relative high exposure to incense smoke in the home, which was restricted primarily to smokers. We also found preliminary evidence that radon exposure might increase risk among smokers with high incense exposure, but power was limited. Our study suggests that exposure to incense smoke in the home may increase the risk of lung cancer among smokers and that exposure to radon may further increase risk. Our study strongly suggests that efforts to prevent lung cancer in the community should include the reduction or minimization of exposures to indoor air pollutants, as well as smoking cessation.
Chan-Yeung M, Koo LC, Ho JC, Tsang KW, Chau WS, Chiu SW, et al. 2003. Risk factors associated with lung cancer in Hong Kong. Lung Cancer 40:131-140.
Chen CC, Lee H. 1996. Genotoxicity Genotoxic substances are a type of carcinogen, specifically those capable of causing genetic mutation and of contributing to the development of tumors. This includes both certain chemical compounds and certain types of radiation. and DNA adduct A DNA adduct is an abnormal piece of DNA covalently-bonded to a cancer-causing chemical. This has shown to be the start of a cancerous cell, or carcinogenesis. DNA adducts in scientific experiments are used as bio-markers and as such are themselves measured to reflect formation of incense smoke condensates: comparison with environmental tobacco smoke condensates. Mutat Res 367:105-114.
Chen CJ, Wu HY, Chuang YC, Chang AS, Luh KT, Chao HH, et al. 1990. Epidemiologic characteristics and multiple risk factors of lung cancer in Taiwan. Anticancer Res 10:971-976.
Cheng JY, Ng EM. 2007 Body mass index, physical activity and erectile dysfunction Erectile Dysfunction Definition
Erectile dysfunction (ED), formerly known as impotence, is the inability to achieve or maintain an erection long enough to engage in sexual intercourse. : an U-shaped relationship from population-based study. Int J Obesity 31:1571-1578.
Darby S, Hill D, Auvinen A, Barros-Dios JM, Baysson H, Bochicchio F, et al. 2005. Radon in homes and risk of lung cancer; collaborative analysis of individual data from 13 European case-control studies. BMJ BMJ n abbr (= British Medical Journal) → vom BMA herausgegebene Zeitschrift 330:223; doi:10.H36/ bmj.38308.477650.63 [Online 21 December 2004].
Ferris BG. 1978. Epidemiology Standardization Project (American Thoracic thoracic /tho·rac·ic/ (thah-ras´ik) pectoral; pertaining to the thorax (chest).
Of, relating to, or situated in or near the thorax. Society). Am Rev Respir Dis 118:1-120.
Friborg JT, Yuan JM( Wang R, Koh WP, Lee HP, Yu MC. 2008. Incense use and respiratory tract carcinomas: a prospective cohort study. Cancer 113:1676-1684.
Ger LP, Hsu WL, Chen KT, Chen CJ. 1993. Risk factors of lung cancer by histological category in Taiwan. Anticancer Res 13:1491-1500.
Greenland S, Rothman KJ. 1998. Concepts of interaction. In: Modern Epidemiology (Rothman KJ, Greenland S, eds). 2nd ed. Philadelphia:Lippincott-Raven, 329-342.
Ho SS, Yu JZ. 2002. Concentrations of formaldehyde and other carbonyls in environments affected by incense burning. J Environ Monit 4:728-733.
Ho ST. 2010. Radon survey in eleven newly developed estates in Hong Kong. Hong Kong Papers in Design and Development l:5fr-58.Available: http://sunzi.lib.hku.hk/hkjo/view/l/100012.pdf [accessed 12 May 2010].
IARC (International Agency for Research on Cancer). 1988. Man-made Mineral Fibers and Radon. IARC Monogr Eval Carcinog Risk Hum 43:1-300.
IARC (International Agency for Research on Cancer). 2010a. Formaldehyde, 2-Butoxyethanol and 1-ferf-Butoxypropan-2-ol. IARC Monogr Eval Carcinog Risk Hum 88. Available: http://monographs.iarc.fr/ENG/Monographs/vol88/index.php [accessed 5 May 2010].
IARC (International Agency for Research on Cancer). 2010b. Benzene (Group 1). IARC Monogr Eval Carcinog Risk Hum (suppl 7). http://monographs.iarc.fr/ENG/Monographs/suppl7Zsuppl7.pdf [accessed 30 September 2011].
Knol MJ, van der Tweel I, Grobbee DE, Numans ME, Geerlings Ml. 2007. Estimating interaction on an additive scale between continuous determinants in a logistic regression model. Int J Epidemiol 36:1111-1118.
Koo LC, Ho JH. 1996. Diet as a confounder of the association between air pollution and female lung cancer: Hong Kong studies on exposures to environmental tobacco smoke, incense, and cooking fumes as examples. Lung Cancer 14(suppll):S47-S61.
Lee YM. 1997. Territory-wide Indoor Radon Follow-up Survey 1995/96. Hong Kong:Hong Kong Government.
Lin TC, Krishnaswamy G, Chi DS. 2008. Incense smoke: clinical, structural and molecular effects on airway disease. Clin Mol Allergy 6:3; doi:10.1186/1476-7961-6-3 [Online 25 April 2008].
Lu H, Zhu L, Chen S. 2008. Pollution level, phase distribution and health risk of polycyclic aromatic hydrocarbons in indoor air at public places of Hangzhou, China. Environ Pollut 152:569-575.
Lung SC, Kao MC, Hu SC. 2003. Contribution of incense burning to indoor PM)0 and particle-bound polycyclic aromatic hydrocarbons under two ventilation conditions. Indoor Air 13:194-199.
MacLennan R, Da Costa J, Day NE, Law CHf Ng YK, Shanmugaratnam K. 1977. Risk factors for lung cancer in Singapore Chinese, a population with high female incidence rates. Int J Cancer 20:854-860.
Navasumrit P, Arayasiri M, Hiang OM, Leechawengwongs M, Promvijit J, Choonvisase S, et al. 2008. Potential health effects of exposure to carcinogenic compounds in incense smoke in temple workers. Chem Biol Interact 173:19-31.
Schottenfeld D, Beebe-Dimmer J. 2010. Chronic inflammation: a common and important factor in the pathogenesis of neoplasia neoplasia /neo·pla·sia/ (-pla´zhah) the formation of a neoplasm.
cervical intraepithelial neoplasia . CA Cancer J Clin 56:69-83.
Tang L, Urn WY, Eng P, Leong SS, Urn TK, Ng AWK (Aho Weinberger Kernighan) A Unix programming utility developed in 1977 by Alfred Aho, Peter Weinberger and Brian Kernighan. Due to its unique pattern-matching syntax, awk is often used in data retrieval and data transformation. , et al. 2010. Lung cancer in Chinese women: evidence for an interaction between tobacco smoking and exposure to inhalants in the indoor environment. Environ Health Perspect 118:1257-1260.
Tse LA, Yu IT, Au JS, Yu KS, Kwok KP, Qiu H, et al. 2009. Environmental tobacco smoke and lung cancer among Chinese nonsmoking males: might adenocarcinoma be the culprit? Am J Epidemiol 169:533-541.
Wang B, Lee SC, Ho KF, Kang YM. 2007. Characteristics of emissions of air pollutants from burning of incense in temples, Hong Kong. Sci Total Environ 377:52-60.
WHO (World Health Organization). 2009. Radon and Cancer. Available: http://www.who.int/mediacentre/factsheets/fs291/en/index.html [accessed 8 November 2010],
Yu IT, Chiu YL, Au JS, Wong TW, Tang JL 2006a. Dose-response relationship between cooking fumes exposures and lung cancer among Chinese nonsmoking women. Cancer Res 66:4961-4967.
Yu IT, Tse LA. 2006b. Exploring the joint effects of silicosis silicosis (sĭlĭkō`sĭs), occupational disease of the lungs caused by inhalation of free silica (quartz) dust over a prolonged period of time. and smoking on lung cancer risks. Int J Cancer 120:133-139.
Lap Ah Tse,1 Ignatius Tak-sun Yu,1 Hong Qiu,1 Joseph Siu Kai Auf2 and Xiao-rong Wang1
1School of Public Health and Primary Care, The Chinese University of Hong Kong, Hong Kong Special Administrative Region A special administrative region may be:
Address correspondence to I. T-S Yu, School of Public Health and Primary Care, The Chinese University of Hong Kong, 4/F School of Public Health, Prince of Wales Hospital
SAR - segmentation and reassembly , China. Telephone: 852-2252-8773. Fax: 852-2606-3500. E-mail:firstname.lastname@example.org
The work described in this article was substantially supported by a grant from the Research Grants Council of die Hong Kong Special Administrative Region, China (project CUHK4460/03M).
The funding source had no role in the study design, data collection, data analysis, or interpretation of the findings.
The authors declare they have no actual or potential competing financial interests.
Received 28 July 2010; accepted 22 July 2011.