Correction
29 Dec 2016: Ji EH, Sun B, Zhao T, Shu S, Chang CH, et al. (2016) Correction: Characterization of Electronic Cigarette Aerosol and Its Induction of Oxidative Stress Response in Oral Keratinocytes. PLOS ONE 11(12): e0169380. https://doi.org/10.1371/journal.pone.0169380 View correction
Figures
Abstract
In this study, we have generated and characterized Electronic Cigarette (EC) aerosols using a combination of advanced technologies. In the gas phase, the particle number concentration (PNC) of EC aerosols was found to be positively correlated with puff duration whereas the PNC and size distribution may vary with different flavors and nicotine strength. In the liquid phase (water or cell culture media), the size of EC nanoparticles appeared to be significantly larger than those in the gas phase, which might be due to aggregation of nanoparticles in the liquid phase. By using in vitro high-throughput cytotoxicity assays, we have demonstrated that EC aerosols significantly decrease intracellular levels of glutathione in NHOKs in a dose-dependent fashion resulting in cytotoxicity. These findings suggest that EC aerosols cause cytotoxicity to oral epithelial cells in vitro, and the underlying molecular mechanisms may be or at least partially due to oxidative stress induced by toxic substances (e.g., nanoparticles and chemicals) present in EC aerosols.
Citation: Ji EH, Sun B, Zhao T, Shu S, Chang CH, Messadi D, et al. (2016) Characterization of Electronic Cigarette Aerosol and Its Induction of Oxidative Stress Response in Oral Keratinocytes. PLoS ONE 11(5): e0154447. https://doi.org/10.1371/journal.pone.0154447
Editor: Muy-Teck Teh, Queen Mary University of London, UNITED KINGDOM
Received: September 8, 2015; Accepted: April 13, 2016; Published: May 25, 2016
Copyright: © 2016 Ji et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: All relevant data are within the paper.
Funding: The authors received no specific funding for this work.
Competing interests: The authors have declared that no competing interests exist.
Introduction
Electronic cigarettes (ECs) are battery-operated devices for a user to inhale an aerosol rather than cigarette smoke. ECs typically have a heating element that generates aerosols by atomizing a liquid solution known as E-liquid, which usually contain a mixture of selected level of nicotine, propylene glycol or glycerin as solvent, and flavors additives. Awareness and use of ECs have greatly increased in the past few years, particularly among young people and women [1]. Although ECs have been proposed as long-term substitutes for traditional smoking or as a tool for smoking cessation, scarce experimental data are available on their safety and health related risks [2]. Most of the current studies are focused on understanding EC users’ behavior or pathological symptoms through the use of approaches including questionnaires compiled by the EC users, surveys from online forums or systematic review of published literature [2–4]. While studies have suggested that the use of ECs substantially decreased cigarette consumption without causing significant side effects in smokers not intending to quit [5], others emphasized that the health effects caused by EC use are not well understood and there is a wide range of reported positive and negative health effects. While the use of the EC may help reduce the number of cigarettes smoked and withdrawal symptoms, the effects are mainly related to a short period of use, and data on long-term efficacy and safety of ECs is currently lacking, which will be of utmost importance to form the basis for guidelines and regulatory decisions on ECs [3, 4].
While the effects of conventional cigarette smoke on human health have been well documented through in vitro and in vivo model studies, little direct work has been done to understand the health risks of ECs, particularly those on the oral cavity. A recent study on E-liquids demonstrated that menthol additives of E-liquid show a harmful effect on human periodontal ligament fibroblasts. The incubation with menthol-flavored E-liquids led to a significant reduction of cell proliferation and viability, which might indicate that menthol additives should be avoided for ECs [6]. Although E-liquid itself is not the same as EC aerosol generated after heating, this study highlights the importance of investigating oral health-related effects of ECs. So far, studies of ECs at molecular levels have been performed on lung/airway epithelia cells. E-liquid has been found to increase inflammation and virus infection in primary human airway epithelial cells [7]. Exposure to ECs impairs pulmonary anti-bacterial and anti-viral defenses in a mouse model, and vapors produced by ECs and E-liquids with flavorings induce toxicity, oxidative stress, and inflammatory response in lung epithelial cells and in mouse lung [8, 9]. Nevertheless, to the best of our knowledge, there is essentially no data describing the effects of EC aerosols on oral epithelial cell function and mechanisms involved in inducing the effects.
In this study, we have generated and characterized EC nanoparticles in gas and liquid phases using a combination of advanced technologies. By using in vitro high-throughput cytotoxicity assays and quantitative PCR (qPCR), we have further demonstrated that EC aerosols significantly decrease intracellular levels of glutathione (GSH) in NHOKs in a dose-dependent fashion, induce the expression of heme oxygenase 1 (HO-1) and cause cytotoxicity to normal oral epithelial cells. This suggests that EC aerosols may induce oxidative stress response and toxicological outcomes in the oral cavity.
Materials and Methods
Cell culture
Normal human oral keratinocytes (NHOKs) were maintained in EpiLife culture media supplemented with the human keratinocyte growth supplement (Invitrogen, Carlsbad, CA, USA), as described previously [10]. The cell line was provided by Dr. Wei Chen at the University of California, Los Angeles. NHOKs were treated with the EC aerosol-impinged EpiLife culture media for 24 hours prior to harvesting of cells for the analysis. Generation of EC aerosols and EC aerosol-impinged cultured media are described below in details.
Generation of EC aerosols
E-liquid with different nicotine strength and flavors were used to generate EC aerosols. A homemade puffing machine composed of a compressed air source, a solenoid valve, and a Raspberry Pi (Raspberry Pi Foundation, UK), which serves as a timer and solenoid valve controller, was used to puff the ECs by pushing clean air through the EC from the front air hole. A piece of Python code running on the Raspberry Pi, which can be adjusted by changing the code, accurately controlled the puff duration and puff interval. The flow rate of the inlet air was calibrated by a flow meter DC-Lite (Drycal, Bios Inc., US). Particle number concentration (PNC) and size distribution of EC aerosols were measured as a function of puff duration from approximately 2 to 5 seconds inside a 320 L stainless-steel chamber. The chamber was tightly closed to avoid air exchange with ambient air. During the experimental period, the relative humidity and temperature inside the chamber were controlled at 30 ± 10% and 24 ± 1°C, respectively. Details of the experiment set up can be found elsewhere [11].
Measurement of particle number concentration and size distribution
The particle number concentration and size distribution of EC aerosols were measured by a Condensation Particle Counter (CPC 3785, TSI Inc., Shoreview, MN) and an Scanning Mobility Particle Sizer (SMPS 3080, TSI Inc., Shoreview, MN), respectively. The sampling flow rate of the SMPS was 0.6 L/min and the measurement range was 7–289 nm (100 s up scan, 20 s down scan). The SMPS starts to work right after each puff. The particle measurements were all repeated five times for each puff duration. After each measurement, the chamber was flushed by clean air until the total particle number concentration in the chamber was less than 1000 cm-3.
Physicochemical characterization of EC particles in liquid
For the liquid phase particle size distribution, the EC aerosols were impinged into liquid (water or culture media) for 10 min, by using the same puffing system at the same flow rate, 1 L/min. High throughput dynamic light scattering (HT-DLS, Dynapro™ Plate Reader, Wyatt Technology) was performed to determine the particle size and size distribution of the EC aerosols in water and cell culture media. Transmission electron microscopy (TEM), using a JEOL 1200 EX (accelerating voltage 80 kV), was used to observe the morphology and to determine the primary size of EC aerosol nanoparticles. Elemental analysis of the EC aerosols were determined by energy-dispersive X-ray spectroscopy (EDX) using a FEI Titan 80/300 microscope. Quantitative elemental analysis of the EC aerosols was determined by inductively coupled plasma optical emission spectrometry (ICP-OES). 500 μL of the impinged EC sample was digested by 3 mL of concentrated nitric acid at 90°C for 3 h. The digested solution was dried by evaporation at 120°C, and 8 mL of 5% nitric acid was added for ICP-OES measurement.
Cytotoxicity assays
The cytotoxicity of EC aerosols in NHOK cells was determined by a ATP assay using the ATPliteTM firstep (Perkin-Elmer, Boston, MA) [12]. After 24 h exposure to EC aerosol-impinged culture medium in a 96-well plate, the culture medium was removed, and cells were washed three times with PBS and incubated with 100 μL of reconstituted ATPlite firstep reagent for 10 min. The luminescence intensity was recorded on a SpectraMax M5 microplate spectrophotometer (Molecular Devices, Sunnyvale, CA).
Determination of intracellular GSH
A GSH-Glo assay kit (Promega, Madison, WI) was used to determine the intracellular GSH levels after EC aerosol exposure in NHOKs [13]. The NHOKs were exposed to EC aerosol particles in a 96-well plate at 37°C and 5% CO2 for 24 h. After exposure, the cellular supernatant was removed and 100 μL of GSH-Glo reaction buffer containing Luciferin-NT and glutathione S-transferase was added to each well in the plate and incubated at room temperature with constant shaking for 30 min. Then, 100 uL of Luciferin D detection reagent was added to each well and the plate was incubated at room temperature with constant shaking for another 15 min. The luminescent signal was quantified using a SpectraMax M5 microplate reader (Molecular Devices; Sunnyvale, CA).
Quantitative real time PCR
Total RNA was isolated from cultured cells using the RNeasy Mini Kit (Qiagen, Valencia, CA). With Superscript II reverse transcriptase (Invitrogen, #18064–022), 1.5μg of RNA per sample was converted into cDNA. The primers sequences were: HO-1-F, CAGGCAGAGAATGCTGAGTT; HO-1-R, GCTTCACATAGCGCTGCA; NRF-2-F, CGGTATGCAACAGGACATTG; NRF-2-R, ACTGGTTGGGGTCTTCTGTG; β-actin-F, GCGCGGCTACAGCTTCA; β-actin-R, CTTAATGTCACGCACGATTTCC. To quantify HO-1 and NRF-2 gene expression levels in untreated and EC aerosol-treated NHOK samples, 1μl of diluted cDNA solution (1:10) was mixed with primers, nucleotides and the SYBR Green I MasterMix (Roche, Indianapolis, IN) in a 96 well PCR plate and the reaction was performed on a CFX96 qPCR system (Bio-Rad, Hercules, CA).
Results
Puff duration and particle number concentration (PNC) of EC aerosols
We have generated EC aerosols and measured PNC and size distribution as a function of puff duration from approximately 2 to 5 seconds. The results are presented in Fig 1, which shows a strong positive correlation (R2 = 0.99) between puff duration and PNC.
Particle number was determined by Condensation Particle Counter (CPC).
PNC and size distribution of EC aerosols at different flavors and nicotine strength
The PNC and size distribution of EC aerosols of different flavors and nicotine strength were also compared (Fig 2). The menthol-flavored EC generates particles with larger sizes (33 nm) compared to the tobacco flavors (25 nm). It also appears to have generated fewer nanoparticles than the tobacco flavored by 13–35%. Compared to zero nicotine, at 24 mg/ml nicotine level, the tobacco flavored showed 9% increase in PNC, but the menthol flavored had approximately 20% decrease in PNC.
Characterization of EC nanoparticles in liquid phase
To perform in vitro cellular studies with NHOKs, the EC aerosol was impinged into the culture medium for NHOK (KGM medium with human keratinocyte growth supplement) for 10 min. Since the suspension of the aerosol particles in aqueous solution will likely change their physicochemical properties, we compared the hydrodynamic size distribution of EC aerosols in NHOK culture medium, DMEM medium and water (different dispersion media) using high-throughput dynamic light scattering analysis (DLS) (Fig 3). Our data indicate that when the EC particles were impinged in water, their hydrodynamic size is around 1181.1±340.1 nm. In contrast, when they were prepared in NHOK culture media, their hydrodynamic size is significantly reduced to 442.3 nm (Table 1), which reflects the dispersion effect of proteins including growth factors that are present in the culture media as a result of the formation of a protein corona on the particle surface that provides electrostatic hindrance preventing agglomeration. When the EC particles were impinged in DMEM medium containing fetal bovine serum, the hydrodynamic size is further reduced to 328.5±9.1 nm, due to dispersal effect of fetal bovine serum as a result of the formation of a protein corona on the particle surface, which contributes to the suspension stability [14]. Fig 4A shows the transmission electron microscope (TEM) image, revealing the flake-like morphology of EC aerosol nanoparticles in the water. Furthermore, energy-dispersive X-ray spectroscopy (EDX) was used to determine the elemental components of EC aerosols (Fig 4B). Silicon (Si), iron (Fe), and sodium (Na) were found in the EC particles. Copper (Cu) was also found but it came from the TEM grid, not the nanoparticles. Quantitative assessment of EC aerosols by inductively coupled plasma optical emission spectrometry (ICP-OES) further confirms the EDX analysis. Besides the elements identified by EDX, ICP-OES also shows the existence of calcium (Ca), magnesium (Mg), and sulfur (S) (Table 2).
Cell media 1: DMEM with fetal bovine serum. Cell media 2: EpiLife media with growth supplement. Hydrodynamic size of EC aerosols was determined using high throughput dynamic light scattering (HT-DLS).
(A) TEM analysis of EC aerosol nanoparticles in water. (B) EDX analysis of EC aerosols that identified elemental composition of EC nanoparticles.
EC aerosol-induced oxidative stress response and cytotoxicity in oral epithelial cells
In vitro analysis of EC aerosol-treated NHOKs show that EC aerosols are capable of inducing oxidative stress as indicated by significant decrease of intracellular glutathione (GSH) levels (Fig 5A). Similar to previously published data [15], the use of fumed silica as a positive control demonstrated a significant decrease in cellular GSH in NHOKs. GSH level decrease is also dose-dependent (Fig 5B). Oxidative stress represents a dynamic equilibrium between antioxidant defense that acts to restore redox equilibrium and oxidant injury responses that can result in toxicological outcomes. We found the injurious oxidative stress in NHOKs leads to significant cytotoxicity as indicated by the ATP assay (Fig 5C). As shown in Fig 5D, qPCR analysis demonstrated that EC aerosols induced the expression of HO-1 in NHOKs, but NRF-2 expression was not significantly altered (Fig 5E).
(A) Intracellular GSH levels in NHOKs after exposure to EC aerosols. NHOKs were exposed to EC aerosols for 24 h and intracellular GSH levels were determined using a GSH-Glo assay. Fumed silica (100 μg/ml) was used as a positive control. *p<0.05 compared to untreated control cells. (B) Heat maps to show the dose-dependent increase in oxidative stress induced by EC in NHOKs. Conditions are the same as (A). (C) Cell viability of NHOKs after exposure to EC aerosols for 24 h was determined using ATP assay. The cell viability of the EC-treated cells was normalized to the value of non-treated control cells, for which the viability was regarded as 100%. Fumed silica (100 μg/ml) was used as a positive control. *p<0.05 compared to untreated control cells. (D&E) qPCR analysis of heme oxygenase 1 (HO-1) and nuclear factor (erythroid-derived 2)-like 2 (NRF-2) expression in NHOKs after exposure to EC aerosols. *p<0.05; ** p<0.01 compared to untreated control cells.
Discussion
EC creates aerosols that consist of nanoparticles and contain small amount of chemicals that may cause toxicological outcome to human oral cavity. Smoking characteristics such as puffing topography or EC device voltage and physicochemical characteristics of vaporized nicotine and other chemical products in ECs are profoundly different when compared to conventional cigarettes. How these toxic substances/nanoparticles from EC aerosols and related smoking/physicochemical characteristics affect the oral cavity remains largely unknown. Considering the increasing popularity of ECs in the general population, there is an urgent need to characterize EC aerosols and assess their biological hazard on oral epithelial cells.
In this study, an impinging method was chosen because it minimizes EC aerosols loss due to evaporation, which is inevitable if filter collection method is used [16, 17]. In addition, impinging method allows EC aerosols to be directly captured in the medium and avoids intermediate steps such as extraction, which are necessary if a filter trapping is used.
Previous studies have shown significant amounts of nanoparticles are present in EC aerosols [16, 18–20]. These observed PNC in gas phase ranged from 1.8×109 cm-3 to 8.4×109 cm-3 and count median diameter (CMD) ranged from 14 nm to 458 nm. Puffing topography and device voltage of ECs have been found to affect EC aerosol characteristics. Fuoco et al. reported that longer puff duration was associated with higher PNC [20]. This has been confirmed by our studies (Fig 1). Ohta et al. [21] measured carbonyls emitted from ECs at voltages from 1.5 V to 7.5 V and found increased carbonyl levels when the voltage was above 3 V. In addition, our studies indicate that the PNC and size distribution of EC aerosol emissions may vary with different flavors and nicotine strength (Fig 2). The menthol flavored EC generated particles with larger sizes compared to the tobacco flavors. It also produced fewer nanoparticles than the tobacco flavored EC. Nicotine levels appeared to affect the PNC differently from the menthol flavor. Compared to zero nicotine, the tobacco flavored EC showed a 9% increase in PNC at 24 mg/ml nicotine level, while the menthol flavored EC had approximately 20% decrease in PNC. In contrast, Fuoco and colleagues reported that flavors did not significantly change the PNC [22]. However, they did find that the PNC significantly increased when nicotine levels in E-liquid are higher, which agrees with our measurements for the tobacco flavor. These finding demonstrates the complexity and knowledge gap in EC aerosol characteristics and highlights the importance to systematically evaluate the impacts of puff duration, EC device voltage and E-liquid composition on EC aerosol characteristics. This information might be important to link the physicochemical properties of EC aerosols under controlled conditions to the biological/toxicological outcomes to the oral cavity.
We also measured the size of EC aerosol nanoparticles in liquid phase. EC aerosols were impinged into water or the cell culture medium for NHOKs and the nanoparticles present in the culture medium were measured with TEM. The EC nanoparticles in liquid phase appeared to be significantly larger than those in the gas phase (Fig 3), and this might be due to aggregation of nanoparticles in the liquid phase. The difference in EC aerosol size distribution and aggregation status between the air and aqueous solution needs to be investigated because it may generate differential toxicological outcomes to cells.
Small trace amount of toxic chemicals and metals were found in the E-liquid and EC aerosols in previously reported studies. For example, formaldehyde, which is assumed to be the product of thermal dehydration of the glycerin or glycols, was detected in EC aerosols [23–25]. However, another study suggested that the formaldehyde may come from exhaled breath rather than from the ECs [16]. Diethylene and ethylene glycol were detected as impurities in E-liquid [26] and in EC aerosols [27]. However, the prevalence of these impurities in E-liquid remains unclear. Kim and Shin [28] found substantial amounts of tobacco specific nitrosamines (TSNA) which are carcinogenic, while McAuley and colleagues [27] detected that TSNA in EC aerosols were at least six times lower than in tobacco smoke. In addition, heavy metal nanoparticles (i.e. Sn, Ag, Fe, Ni, Al, Cr) were found in EC aerosols which could be resulted from the oxidation of the heating coil [29]. We also examined the elemental components of the EC nanoparticles in the liquid phase and Fe, Si and Na were detected with the EDX analysis. Due to their unique physicochemical properties including high surface area, metal/metal oxide nanoparticles exhibit higher dissolution rate or surface reactivity compared to their bulk form. Our previous studies revealed that metal/metal oxide nanoparticles could cause oxidative stress and cytotoxicity in vitro and acute lung inflammation in vivo [12, 30]. The exact role of particles in EC-induced cytotoxicity needs to be determined in future studies.
There is a practical challenge when studying the physicochemical characteristics of EC aerosols. Due to the chemical complexity of EC aerosols, it appears to be very difficult to link a specific chemical component of EC aerosols to the toxicological outcomes. As reported earlier, cigarette smoke is a complex mixture consisting of more than 5600 identified chemical constituents of which approximately 150 have been identified so far as “tobacco smoke toxicants” [31, 32]. This can be partially solved by including well-characterized controls (e.g., metal/metal oxide nanoparticles) [12]. Trace metals or chemicals identified by other instrumental analysis methods (e.g., ICP or LC/GC-MS) would provide useful information on the potential toxic components in EC aerosols, and by including reference standards for in vitro studies, we might be able to identify major toxic components in EC aerosols.
More importantly, our data suggest that EC aerosols may cause cytotoxicity to human oral keratinocytes via oxidative stress response. High-throughput cytotoxicity assays confirmed that EC aerosols are capable of inducing oxidative stress in NHOKs as indicated by significant dose-dependent decrease of intracellular GSH levels. We also found the injurious oxidative stress causes cytotoxicity of NHOKs as indicated by the ATP assay. In addition, similar to our previous studies on the toxicology of nanoparticles [12, 33], HO-1 expression was found to be induced in NHOKs by EC aerosols, which correlate well with the high-throughput cytoassay data on decreased intracellular GSH level and cytotoxicity.
As a summary, we have prepared and measured PNC and size distribution of EC aerosols in the gas phase and found that there is a strong positive correlation between puff duration and PNC. We have also characterized the hydrodynamic size of EC nanoparticles in liquid phase (water and cell cultured media) and determined their elemental composition. Because PNC, particle size and chemical content are highly relevant to the toxicity of EC aerosols, it is important to characterize these physiochemical parameters and understand the effect of smoking characteristics such as puff duration and device voltage on these physiochemical parameters. Our in vitro assays have shown that EC aerosols could cause oxidative stress responses and induce cytotoxicity in oral epithelial cells. These data suggest that EC aerosols damage human keratinocytes in vitro, and the underlying molecular mechanisms may be or at least partially due to oxidative stress and inflammation responses induced by toxic substances (e.g., nanoparticles and chemicals) present in EC aerosols. Therefore, further safety assessment of toxicological and pathological effects of EC aerosols on human health is certainly important. In the future, our research focus is to investigate pathological effects and oxidative stress/inflammation responses in the animal models caused by EC aerosol exposure.
Author Contributions
Conceived and designed the experiments: TX YZ DM SH. Performed the experiments: EHJ BS TZ SS CHC. Analyzed the data: BS EHJ TX YZ SH. Contributed reagents/materials/analysis tools: BS EHJ TZ SS CHC. Wrote the paper: TX YZ SB SH.
References
- 1. Schraufnagel DE, Blasi F, Drummond MB, Lam DCL, Latif E, Rosen MJ, et al. Electronic Cigarettes. A Position Statement of the Forum of International Respiratory Societies. American Journal of Respiratory and Critical Care Medicine. 2014;190(6):611–8. pmid:25006874
- 2. Manzoli L, La Vecchia C, Flacco ME, Capasso L, Simonetti V, Boccia S, et al. Multicentric cohort study on the long-term efficacy and safety of electronic cigarettes: study design and methodology. BMC public health. 2013;13:883. pmid:24063569
- 3. Hua M, Alfi M, Talbot P. Health-related effects reported by electronic cigarette users in online forums. Journal of medical Internet research. 2013;15(4):e59. pmid:23567935
- 4. Gualano MR, Passi S, Bert F, La Torre G, Scaioli G, Siliquini R. Electronic cigarettes: assessing the efficacy and the adverse effects through a systematic review of published studies. Journal of public health (Oxford, England). 2015;37(3):488–97.
- 5. Polosa R, Caponnetto P, Morjaria JB, Papale G, Campagna D, Russo C. Effect of an electronic nicotine delivery device (e-Cigarette) on smoking reduction and cessation: a prospective 6-month pilot study. BMC public health. 2011;11:786. pmid:21989407
- 6. Willershausen I, Wolf T, Weyer V, Sader R, Ghanaati S, Willershausen B. Influence of E-smoking liquids on human periodontal ligament fibroblasts. Head & face medicine. 2014;10:39.
- 7. Wu Q, Jiang D, Minor M, Chu HW. Electronic Cigarette Liquid Increases Inflammation and Virus Infection in Primary Human Airway Epithelial Cells. PLoS ONE. 2014;9(9):e108342. pmid:25244293
- 8. Lerner CA, Sundar IK, Yao H, Gerloff J, Ossip DJ, McIntosh S, et al. Vapors Produced by Electronic Cigarettes and E-Juices with Flavorings Induce Toxicity, Oxidative Stress, and Inflammatory Response in Lung Epithelial Cells and in Mouse Lung. PLoS ONE. 2015;10(2):e0116732. pmid:25658421
- 9. Sussan TE, Gajghate S, Thimmulappa RK, Ma J, Kim J-H, Sudini K, et al. Exposure to Electronic Cigarettes Impairs Pulmonary Anti-Bacterial and Anti-Viral Defenses in a Mouse Model. PLoS ONE. 2015;10(2):e0116861. pmid:25651083
- 10. Zhang M, Chai Y, Brumbaugh J, Liu X, Rabii R, Feng S, et al. Oral cancer cells may rewire alternative metabolic pathways to survive from siRNA silencing of metabolic enzymes. BMC Cancer. 2014;14(1):223.
- 11.
Zhao T, Shu S, Guo Q, Zhu Y. Effects of manufacturing parameters and puff topography on the heating coil temperature and mainstream particles in electronic cigarettes Environmental Science & Technology. 2016;submitted.
- 12. Zhang H, Ji Z, Xia T, Meng H, Low-Kam C, Liu R, et al. Use of Metal Oxide Nanoparticle Band Gap to Develop a Predictive Paradigm for Oxidative Stress and Acute Pulmonary Inflammation. ACS nano. 2012;6(5):4349–68. pmid:22502734
- 13. Sun B, Ji Z, Liao Y-P, Wang M, Wang X, Dong J, et al. Engineering an Effective Immune Adjuvant by Designed Control of Shape and Crystallinity of Aluminum Oxyhydroxide Nanoparticles. ACS Nano. 2013;7(12):10834–49. pmid:24261790
- 14. Nel AE, Maedler L, Velegol D, Xia T, Hoek EMV, Somasundaran P, et al. Understanding Biophysicochemical Interactions at the Nano-Bio Interface. Nature Materials. 2009;8(7):543–57. pmid:19525947
- 15. Sun B, Pokhrel S, Dunphy DR, Zhang H, Ji Z, Wang X, et al. Reduction of Acute Inflammatory Effects of Fumed Silica Nanoparticles in the Lung by Adjusting Silanol Display through Calcination and Metal Doping. Acs Nano. 2015, 9(9):9357–72. pmid:26200133
- 16. Schripp T, Markewitz D, Uhde E, Salthammer T. Does e-cigarette consumption cause passive vaping? Indoor air. 2013;23(1):25–31. pmid:22672560
- 17. Geiss O, Bianchi I, Barahona F, Barrero-Moreno J. Characterisation of mainstream and passive vapours emitted by selected electronic cigarettes. International journal of hygiene and environmental health. 2015;218(1):169–80. pmid:25455424
- 18. Laugesen M, editor Ruyan e-cigarette bench-top tests. Poster presented at the Conference of the Society for Research on Nicotine and Tobacco Dublin, April 27–30; 2009.
- 19. Ingebrethsen BJ, Cole SK, Alderman SL. Electronic cigarette aerosol particle size distribution measurements. Inhalation toxicology. 2012;24(14):976–84. pmid:23216158
- 20. Fuoco F, Buonanno G, Stabile L, Vigo P. Influential parameters on particle concentration and size distribution in the mainstream of e-cigarettes. Environmental Pollution. 2014;184:523–9. pmid:24172659
- 21. Ohta K, Uchiyama S, Inaba Y, Nakagome H, Kunugita N. Determination of Carbonyl Compounds Generated from the Electronic Cigarette Using Coupled Silica Cartridges Impregnated with Hydroquinone and 2,4-Dinitrophenylhydrazine. Bunseki Kagaku. 2011;60(10):791–7.
- 22. Fuoco FC, Buonanno G, Stabile L, Vigo P. Influential parameters on particle concentration and size distribution in the mainstream of e-cigarettes. Environmental Pollution. 2014;184(SI):523–9.
- 23. Goniewicz ML, Knysak J, Gawron M, Kosmider L, Sobczak A, Kurek J, et al. Levels of selected carcinogens and toxicants in vapour from electronic cigarettes. Tob Control. 2014;23(2):133–9. pmid:23467656
- 24. Uchiyama S, Ohta K, Inaba Y, Kunugita N. Determination of carbonyl compounds generated from the E-cigarette using coupled silica cartridges impregnated with hydroquinone and 2, 4-dinitrophenylhydrazine, followed by high-performance liquid chromatography. Analytical Sciences. 2013;29(12):1219–22. pmid:24334991
- 25. Pellegrino R, Tinghino B, Mangiaracina G, Marani A, Vitali M, Protano C, et al. Electronic cigarettes: an evaluation of exposure to chemicals and fine particulate matter (PM). Annali di igiene: medicina preventiva e di comunita. 2012;24(4):279–88.
- 26.
F.D.A. Summary of Results: Laboratory Analysis of Electronic Cigarettes Conducted by FDA. Silver Spring, MD: Food and Drug Administration (FDA); 2009. http://www.fda.gov/NewsEvents/PublicHealthFocus/ucm173146.htm.
- 27. McAuley TR, Hopke PK, Zhao J, Babaian S. Comparison of the effects of e-cigarette vapor and cigarette smoke on indoor air quality. Inhalation Toxicology. 2012;24(12):850–7. pmid:23033998
- 28. Kim HJ, Shin HS. Determination of tobacco-specific nitrosamines in replacement liquids of electronic cigarettes by liquid chromatography-tandem mass spectrometry. Journal of Chromatography A. 2013;1291:48–55. pmid:23602640
- 29. Williams M, Villarreal A, Bozhilov K, Lin S, Talbot P. Metal and silicate particles including nanoparticles are present in electronic cigarette cartomizer fluid and aerosol. 2013;8(3):e57987
- 30. Wang X, Ji Z, Chang CH, Zhang H, Wang M, Liao Y-P, et al. Use of Coated Silver Nanoparticles to Understand the Relationship of Particle Dissolution and Bioavailability to Cell and Lung Toxicological Potential. Small. 2014;10(2):385–98. pmid:24039004
- 31. Garcia-Canton C, Anadon A, Meredith C. Genotoxicity evaluation of individual cigarette smoke toxicants using the in vitro γH2AX assay by High Content Screening. Toxicology Letters. 2013;223(1):81–7. pmid:24021168
- 32. Cunningham FH, Fiebelkorn S, Johnson M, Meredith C. A novel application of the Margin of Exposure approach: Segregation of tobacco smoke toxicants. Food and Chemical Toxicology. 2011;49(11):2921–33. pmid:21802474
- 33. Xia T, Kovochich M, Liong M, Madler L, Gilbert B, Shi H, et al. Comparison of the Mechanism of Toxicity of Zinc Oxide and Cerium Oxide Nanoparticles Based on Dissolution and Oxidative Stress Properties. ACS nano. 2008;2(10):2121–34. pmid:19206459