| Literature DB >> 25480544 |
Sumit R Kumar1, Shelby Davies1, Michael Weitzman2, Scott Sherman3.
Abstract
OBJECTIVE: There has been a rapid increase in the use of waterpipe tobacco and non-tobacco based shisha in many countries. Understanding the impact and effects of second-hand smoke (SHS) from cigarette was a crucial factor in reducing cigarette use, leading to clean indoor air laws and smoking bans. This article reviews what is known about the effects of SHS exposure from waterpipes. DATA SOURCES: We used PubMed and EMBASE to review the literature. Articles were grouped into quantitative measures of air quality and biological markers, health effects, exposure across different settings, different types of shisha and use in different countries. STUDY SELECTION: Criteria for study selection were based on the key words related to SHS: waterpipe, hookah, shisha and third-hand smoke. DATA EXTRACTION: Independent extraction with two reviewers was performed with inclusion criteria applied to articles on SHS and waterpipe/hookah/shisha. We excluded articles related to pregnancy or prenatal exposure to SHS, animal studies, and non-specific source of exposure as well as articles not written in English. DATA SYNTHESIS: A primary literature search yielded 54 articles, of which only 11 were included based on relevance to SHS from a waterpipe/hookah/shisha.Entities:
Keywords: Environment; Non-cigarette tobacco products; Secondhand smoke
Mesh:
Substances:
Year: 2014 PMID: 25480544 PMCID: PMC4345792 DOI: 10.1136/tobaccocontrol-2014-052038
Source DB: PubMed Journal: Tob Control ISSN: 0964-4563 Impact factor: 7.552
Figure 1Search strategy algorithm (SHS, second-hand smoke).
Articles obtained from the literature search
| Lead author | Year | Country | Type and number of subjects (or target places) | Study design | Outcomes measured | Summary | Main findings | Exclusion of other sources of second-hand smoke |
|---|---|---|---|---|---|---|---|---|
| Cobb | 2013 | USA | 28 venues in Virginia (17 waterpipe cafes, 5 restaurants permitting cigarette smoking and 6 smoke-free restaurants (5 with valid data)) | Observational | PM with a 2.5 μm aerodynamic diameter or smaller (PM2.5) | Waterpipe café smoking rooms have a hazardous level of PM2.5 that could be potentially harmful to customers and workers | PM2.5 was greater in waterpipe café smoking rooms (374 μg/m3, n=17) compared with waterpipe café non-smoking rooms, cigarette smoking-permitted restaurant smoking rooms, cigarette smoking-permitted restaurant non-smoking rooms, and smoke-free restaurants | Measurements began 5 min prior to entering the venue and ended 5 min after exiting each venue to compare outdoor ambient air to the air inside the venue |
| Daher | 2010 | Lebanon | 4 repeated waterpipe-smoking sessions and 4 repeated cigarette trials | Observational | Sidestream smoke from waterpipes or cigarettes for ultrafine particles, carcinogenic polyaromatic hydrocarbons, volatile aldehydes, and CO | Second-hand waterpipe smoke emits significant harmful substances | Sidestream waterpipe smoke had nearly 4 times the carcinogenic PAH, 4 times the volatile aldehydes and 30 times the CO of 1 cigarette | Smoking-machine and environmental chamber approach allowed for repeated measurements under controlled conditions and few confounding variables |
| Fiala | 2012 | USA | 10 indoor hookah lounges in Oregon | Observational | PM smaller than 2.5 μm in diameter | Air quality in hookah lounges in Oregon ranges from unhealthy to hazardous | 2 hookah lounges had peak PM2.5 measurements in the hazardous EPI air quality category, 4 were very unhealthy, and 4 were unhealthy. None had good air quality | Measurements began prior to entering the venues and ended after exiting the venues to compare the outdoor ambient air to the air in the hookah lounges |
| Fini | 2013 | Iran | 387 total persons (172 male and 215 female) | Observational | Demographic characteristics and questions related to environmental tobacco smoke exposure | A large proportion of citizens of Bandar Abbas city are exposed to environmental tobacco smoke | The most common places that people were exposed to hookah smoke were in the home (93.4%), coffee shops (17.1%) and restaurants (11.5%). People were exposed to environmental cigarette smoke in public vehicles (52.2%) and the home (31.3%) | NA |
| Hammal | 2013 | Canada | 3 replicates of each of the 3 brands were analysed. 6 randomly selected waterpipe cafes were visited | Observational | Chemical constituents of tobacco-free products used in waterpipes, waterpipe emission under controlled conditions, and air quality markers in waterpipe cafes | Second-hand smoke from herbal shisha contains carcinogens equal to or greater than that found in cigarettes and may be hazardous | Second-hand waterpipe smoke had significant levels of aromatic hydrocarbons, CO, PM2.5 and trace metals | Measurements taken outdoors before and after the visit for comparison |
| Kassem | 2014 | USA | 24 homes were visited 3 times during a 7-day period | Observational | Levels of indoor air and surface nicotine, child uptake of nicotine, the carcinogen NNK, and the toxicant acrolein by measuring corresponding metabolites cotinine, NNAL and NNAL-glucuronides and 3-HPMA | Children living in homes of hookah smokers are exposed to nicotine, the carcinogen NNK and the toxicant acrolein, which pose a threat to long-term health | Compared with homes of non-smokers, children living in homes of daily or weekly/monthly hookah smokers had significantly elevated levels of cotinine and NNAL, with children of daily smokers also having significantly elevated 3-HPMA | 2 air samples were collected with passive diffusion monitor badges in the living room and child's bedroom. A blank non-analysed badge was placed in a third room |
| Markowicz | 2014 | Sweden | Filters from 10 replicate sessions of waterpipe smoking | Observational | Microbial compounds in waterpipe smoke | Waterpipe smoke creates a bioaerosol similarly to cigarette smoke | In a 1–2 h session, second-hand smoke from waterpipes produced a concentration of 2.8 pmol/m3 of LPS. Ergosterol was not detected. This is comparable to 22.2 pmol/m3 of LPS and 87.5 ng/m3 of ergosterol from smoking 5 cigarettes | NA |
| Tamim | 2003 | Lebanon | 625 students from 5 different private schools | Observational | Information on demographic, in-home smoking, and students’ respiratory tract illnesses (cough, wheezing, runny nose, or nasal congestion) | Children exposed to second-hand waterpipe smoke may develop respiratory problems | 22.6% (12/53) had wheezing or nasal congestion, 11.3% (6/53) had just wheezing, and 15.1% (8/53) had just nasal congestion | NA |
| Zaidi | 2011 | Pakistan | 39 indoor venues (13 shisha smoking, 13 cigarette smoking, and 13 non-smoking) | Observational | Mean concentration of PM2.5 | Air quality at shisha smoking venues had hazardous air quality | Shisha smoking venues had an average PM2.5 of 1745 μg/m3 | Venues with other sources of indoor air pollution and non-air-conditioned venues exposed to outdoor pollution were excluded. Samples were obtained before entering the venues to calibrate the device |
| Zeidan | 2014 | Lebanon | 147 people surveyed | Observational | Questionnaires on sociodemographic characteristics, respiratory symptoms and exposure to second-hand smoke. Exhaled CO levels | Second-hand waterpipe smoke may cause respiratory symptoms in non-smokers | Of the 147 surveyed, 48 were exposed only to second-hand waterpipe smoke. 58% reported a chronic cough | Measurements of expired-air CO were calibrated with local environmental CO concentration |
| Zhang | 2013 | Canada | Indoor (n=12) and outdoor (n=5) air quality was assessed in Toronto, Canada waterpipe cafes | Observational | Air nicotine, fine PM less than 2.5 μm in diameter, and ambient CO | Air quality of waterpipe cafés is a health hazard. Waterpipe smoking should be eliminated from indoor and outdoor hospitality venues | Indoor values were 1419 µg/m3 for PM2.5, 17.7 ppm for ambient CO, and 3.3 µg/m3 for air nicotine. Outdoor values were 80.5 µg/m3 for PM2.5, 0.5 ppm for ambient CO, and 0.6 µg/m3 for air nicotine | Measurements taken as far as possible from kitchen areas and open windows to reduce contamination. Background readings obtained outdoors in areas without nearby smokers |
3-HPMA, 3-hydroxypropylmercapturic acid; CO, carbon monoxide; EPI, Environmental Performance Index; LPS, lipopolysaccharides; NA, not applicable; NNAL, 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanol; NNK, 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone; PAH, polycyclic aromatic hydrocarbon; PM, particulate matter.