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Article

Exposure to Toxic Compounds Using Alternative Smoking Products: Analysis of Empirical Data

by
Sandra Sakalauskaite
1,*,
Linas Zdanavicius
2,
Jekaterina Šteinmiller
3 and
Natalja Istomina
2,4
1
Laboratory of Immunology, Department of Immunology and Allergology, Lithuanian University of Health Sciences, 50161 Kaunas, Lithuania
2
Faculty of Medicine, Vilnius University, 03101 Vilnius, Lithuania
3
Nursing Department, Tallinn Health Care College, 13418 Tallinn, Estonia
4
Faculty of Public Governance and Business, Mykolas Romeris University, 08303 Vilnius, Lithuania
*
Author to whom correspondence should be addressed.
Int. J. Environ. Res. Public Health 2025, 22(7), 1010; https://doi.org/10.3390/ijerph22071010
Submission received: 9 June 2025 / Revised: 23 June 2025 / Accepted: 24 June 2025 / Published: 26 June 2025
(This article belongs to the Special Issue Human Exposure to Genotoxic Environmental Contaminants)

Abstract

Tobacco control policies have aimed to reduce the global prevalence of smoking. Unfortunately, the recent survey data shows that about 24% of Europeans still smoke. Although combustible cigarettes remain the most used tobacco product, the tendency made evident in the prevalence of smoking-alternative nicotine-containing products increases. Studies that can objectively assess the long-term health effects of the latter products are lacking, so assessing toxic substances associated with smoking-alternative products and comparing them to substances from combustible cigarettes could inform future public health efforts. The manufacturers of these alternative products claim that the use of alternatives to combustible cigarettes reduces exposure to toxic compounds, but the reality is unclear. This study compares the concentrations of toxic substances in generated aerosols and performs calculations based on mainstream cigarette smoke and aerosols from smoking-alternative products. It summarizes the amounts of harmful and potentially harmful constituents per single puff. Alternative smoking products are undoubtedly harmful to non-smokers. Still, based on the analysis of the latest independent studies’ empirical data, the concentrations of inhaled HPHCs using heated tobacco products or e-cigarettes are reduced up to 91–98%, respectively; therefore, for those who cannot quit, these could provide a less harmful alternative. However, more well-designed studies of alternative product emissions are needed, including an analysis of the compounds that are not present in conventional tobacco products (e.g., thermal degradation products of propylene glycol, glycerol, or flavorings) to evaluate possible future health effects objectively.

1. Introduction

Globally, according to the surveys of the World Health Organization, the prevalence of smoking was about 22% in 2020 [1]. An assessment of smoking trends between 1970 and 2020 shows that smoking rates declined by about 15% within the US and several other countries in the Organization for Economic Cooperation and Development (OECD) [2]. Tobacco control policies over the past two decades have aimed to reduce the global prevalence of smoking, but the recent special Eurobarometer 539 survey of 2023 shows that about 24% of people in the EU still smoke. This is only 1% less than in 2021 [3]. Furthermore, according to the World Health Organization (WHO), the tobacco epidemic is one of the world’s biggest public health threats, killing more than 8 million people worldwide every year [4,5]. Tobacco use is associated with the risk of developing a number of diseases: cardiovascular, respiratory and oncological diseases; reproductive health problems; and adverse effects on the immune system [4,6,7]. Smoking cessation is difficult because smoking addiction is caused by physiological (nicotine) and psychological factors (smoking ritual) [8,9]. For these reasons, the search has begun for ways in which smoking behaviour can still be changed to minimise the damage to health. This has led to the development of new products that manufacturers claim are less harmful alternatives to combustible cigarettes (CC). These include non-combustible tobacco products (e.g., heated tobacco products (HTPs), pin heating systems) and nicotine products (e.g., e-cigarettes, nicotine pads) [10,11]. The problem is that alternative products became popular long before there was sufficient scientific evidence to determine their potentially harmful health effects on consumers [12]. Exposure to toxic compounds found in tobacco smoke has been consistently linked to an increased risk of various diseases. While it is widely assumed that reducing exposure to harmful and potentially harmful constituents (HPHCs) would lower disease risk, direct evidence establishing a causal link between reduced exposure and decreased disease incidence remains limited. To date, few studies have systematically evaluated how the use of non-combustible tobacco products influences toxicant exposure levels, and these studies are tobacco industry-dependent [13,14,15,16]. Unfortunately, there is no data about the relationship between exposure to toxicants and disease risk. Nevertheless, the first step is to clarify the level of reduction in toxicant emissions associated with non-combustible tobacco products, based on independent studies. Therefore, our study aims to summarize and compare the emission levels of HPHCs in non-combustible tobacco products, providing a basis for further research studies on the long-term health effects of these products.

1.1. The Combustion Process of the Cigarette

Combustion-based products are the ones most harmful to smokers. Cigarette combustion produces ash and smoke containing particulate matter and large quantities of more than 7000 identified harmful chemicals, of which almost 100 are classified as harmful or potentially harmful because of their association with smoking-related diseases [17,18]. One group of pollutants with carcinogenic and mutagenic properties comprises polycyclic aromatic hydrocarbons (PAHs), which have a temperature-dependent profile: PAH formation starts at temperatures up to 450 °C, with a maximum yield at 500–550 °C. Therefore, if the process is carried out at temperatures below 400 °C, the release of toxic substances is significantly reduced [19,20]. This is the rationale behind the principle of HTPs as an alternative to combustible cigarettes. In non-combustible tobacco products, electronically controlled heating prevents combustion. Natural tobacco containing nicotine is heated and no ash is produced [21,22]. As a result, the smoker inhales an aerosol of heated tobacco. Thus, compared to cigarettes, harmful substances should be formed in lesser quantities, but what is the reality? There is a lack of studies comparing all three products: combustible cigarettes, HTP, and e-cigarettes. Furthermore, it is not easy to compare the levels of inhaled HTP compounds from separate studies because the study conditions need to be taken into account. For this reason, in the present work, we have performed calculations to estimate the levels of inhaled harmful and potentially harmful constituents (HPHCs)-based compounds in different smoking products and compared them with the levels associated with smoke inhaled while cigarette smoking.

1.2. Comparison of the Principles of Operation of HTP and E-Cigarettes

One common problem is that users equate HTPs with e-cigarettes. However, these two products have different principles of operation. In HTPs, the natural tobacco containing nicotine is heated [23]. In contrast, smoking e-cigarettes vaporizes the e-cigarette liquid. This liquid consists of vegetable glycerol (60–70%), propylene glycol (25–30%), nicotine extracted from tobacco (0–6%), and flavorings (5–15%). The glycerol and propylene glycol in e-liquids cause smokers to exhale a large amount of vapor, which is commonly referred to, by users, as smoke. As with HTPs, no ash is produced [24,25,26]. Thus, the main difference between HTPs and e-cigarettes is that the latter uses a vaporized chemical liquid, and the smoker inhales the vapor. In contrast, users of HTPs inhale an aerosol of heated tobacco [23,27,28].

1.3. Comparison of Emissions

The Food and Drug Administration (FDA) of the United States of America has published a list of “Harmful and Potentially Harmful Constituents (HPHCs) in Tobacco Products and Tobacco Smoke”; there are five main groups of compounds in this list: carbonyls, volatile organic compounds, N’-nitrosamines, heterocyclic compounds, and inorganic compounds (metals) [27]. The World Health Organization (WHO) has also published a list of chemicals which are recommended as candidates for mandatory lowering of levels [28,29]. Therefore, in this paper, we will compare the emissions of the most hazardous, high-priority substances present in combustible cigarette smoke and the mainstream aerosol smoking-alternative products and will summarize the data from the latest independent studies.

2. Methods

This research consisted of three steps. First, based on a review of the literature, we collected the emission results for HPHCs in mainstream CC smoke and alternative product aerosols, based on data from independent studies. Then, we converted the concentrations of HPHCs into the concentrations obtained per single puff. Finally, we calculated the reduction in HPHCs emissions using Formulas (1) and (2).

2.1. Criteria for Literature Selection

A comprehensive search was performed across two electronic databases, PubMed and Science Direct, covering publications from January 2014 to May 2025. The search strategy included keywords such as “toxic compounds in cigarette smoke” (result: 456 publications), “toxic compounds in heated tobacco product aerosols” (result: 37 publications), “toxic compounds in e-cigs aerosols” (result: 100 publications), “comparison of emissions from smoking products” (result: 105 publications), and their respective synonyms. To facilitate comparisons of the results, we have chosen only studies that are not associated with the tobacco industry. We have selected studies that employed validated methods, including those conducted under the Health Canada Intense (HCI) and International Organization for Standardization (ISO) regimens. Given that e-cigarette emissions depend on the flavor added, we used the results obtained with tobacco-flavored e-cigarettes and HTP regular products. Fifteen studies met the inclusion criteria and were included for further analysis.

2.2. Data Normalization/Conversion

To date, we were unable to identify any independent studies that simultaneously examined all three smoking products—CC, HTPs, and e-cigarettes. Therefore, the substance concentrations measured by a whole-product unit (CC, HTPs, or e-cigarettes) reported in the reviewed publications were converted, using the available data, to reflect the estimated amount per inhalation (i.e., concentration per puff), enabling standardized comparisons across studies. A reference cigarette, 3R4F, was chosen to objectify the emissions from combustible cigarettes (as a comparator) [30].

2.3. Statistical Analysis Methods

Descriptive statistics, including means, medians, and minimum and maximum values, were calculated using Microsoft Excel 2010 (Microsoft Corporation, Redmond, WA, USA).

The Calculation of the Risk Reduction Potential of HPHCs

The average concentrations per single puff according to the data from different independent studies were calculated. To assess the differences between the levels of toxic compounds in the emissions of the different smoking products, calculations according to Formula (1) below have been applied in the calculation of the reduction:
Reduction   =   ( 1     A v e r a g e   c o n c e n t r a t i o n   o f   t o x i c   c o m p o u n d   i n   H T P   o r   E c i g A v e r a g e   c o n c e n t r a t i o n   o f   t o x i c   c o m p o u n d   i n   C C )   × 100%  
For the deriving the average reduction for all toxic compounds, we applied Formula (2) below:
Average   reduction   =   S u m   o f   t h e   p e r c e n t a g e   r e d u c t i o n s   f o r   e a c h   t o x i c   c o m p o u n d N u m b e r   o f   t o x i c   c o m p o u n d s   a s s e s s e d
The formulas applied in our study are based on standard comparative-assessment logic and are commonly used in exposure reduction evaluations. This approach provides a general indicator of overall emission reduction across a range of analytes when toxicological weighting is not applied.

3. Results

3.1. Comparative Data on Smoking Product Emissions

Based on empirical data from the meta-analysis of scientific research data and scientific articles, median and min-max ranges of the substances’ concentrations per single puff were calculated from the collected data and are shown in Table 1.

3.2. Reduced Emission Profiles of Alternative Products

The results of the reduction calculations are presented in Figure 1. Data analysis showed that the inhaled levels of HPHCs that are released during the combustion process, such as polycyclic aromatic hydrocarbons (PAHs) and volatile organic compounds (VOCs), are reduced 99% and 100% in e-cigarettes and 96% and 99% in HTPs aerosols. The concentrations of inhaled carbonyls are reduced by almost 100% in e-cigarettes and 65–95% in HTPs aerosols. The inhaled concentrations of the most important group of carcinogens in tobacco products—tobacco-specific nitrosamines (TSNAs)—are reduced 99% in e-cigarettes and 89–94% in HTP aerosols. The nicotine and CO concentrations per single puff are reduced by 81% and 99% in e-cigarettes and 82% and 98% in HTPs aerosols, respectively. Some substances in the emissions of the alternative products were under the detection limit (e.g., NAB, NNK, propionaldehyde, crotonaldehyde, VOC, and some metals). Therefore, these reduction rates could not be evaluated. However, such a result showed that the amounts of these substances in the aerosols of mainstream HTPs or E-cigs is reduced compared with CC.

4. Discussion

A smoking reduction strategy aims to reduce the number of smokers, but this is not yet an easy task because quitting smoking is a long-term process, and the risks to smokers’ health need to be reduced as soon as possible. Our analysis of independent studies showed that the concentrations of HPHCs indicated in the FDA and WHO lists are decreased by up to 91% in HTP aerosols and 98% in e-cigarettes, per puff. Such a significant reduction in HPHCs results in a reduced exposure to toxic substances, which in turn leads to fewer adverse health effects for smokers. Still, it is important to note that alternatives to combustible cigarettes are not harmless, and they are targeted to smokers who are unable to quit.
A correctly modeled study design and identical experimental conditions are essential in order to assess the emissions from different tobacco products objectively. However, the analysis of the current data revealed the problem that many studies are inadequately designed, and cannot objectively assess whether the alternatives to combustible cigarettes are less harmful to human health. It was found that the results for the emissions of the reference cigarette were not the same in different studies. This is because the researchers use different methodologies and equipment, which are not necessarily validated, in their studies. In addition, some analytes, such as CO emissions, are associated in e-cigarettes with higher power settings, longer puff durations, and e-liquids with flavors [72]. Thus, when comparing studies, it is important to consider that the differences between results obtained could be due to methodological aspects. Therefore, the emissions of smoking-alternative products should be critically evaluated. It should be noted that there are only two validated regimens of analytical methods for toxic compound determination in smoke: ISO and CI [53]. Thus, evaluations of the alternatives to combustible cigarettes should be based only on studies that use reliable equipment and validated analysis protocols. Furthermore, while evaluating and summarizing the effects of alternative products on human health, the most common errors are small sample sizes and inappropriate comparisons between study groups (comparing non-smokers with smokers). Since there is no doubt that these products have an adverse effect on human health, non-smokers should not be included in the subject groups for the purposes of comparative analysis.
Interestingly, two substances to which not much attention is given are the key components of e-cigarettes, glycerol and propylene glycol, which are not included in the list of “Harmful and Potentially Harmful Constituents (HPHCs) in Tobacco Products and Smoke.” The food industry has long used both compounds as sweeteners or stabilizing agents, and they are considered safe to ingest. However, the consequences of propylene glycol and glycerol inhalation remain unknown. There is data that these compounds are associated with increased upper-airway symptoms and could impact the response to concomitant exposure to pollutants, allergens, and pathogens [73,74,75]. Additionally, the health effects of the thermal degradation products from the flavorings used in E-cigs remain poorly understood. Many flavorings can break down into new compounds during heating, some of which, such as aldehydes or reactive carbonyls, may pose a risk to respiratory health. However, the current scientific evidence on the inhaled amounts and long-term effects of these substances is limited [76,77]. Therefore, these results provide a basis for a deeper examination of the long-term effects of these compounds on human health. It is also important to note that, in parallel to regulated and commercially available products, the spread of non-regulated E-cigs products, which often contain undeclared components, remains a major public health concern. These products are more likely to be accessed by young people and have been implicated in various acute health incidents, underscoring the need for strict market surveillance and regulation.
The limitation affecting our publication is that the data was collected from separate studies, the results of which may have been influenced by technical and methodological differences (e.g., differences in protocols or detection limits). Nevertheless, we have analyzed a large amount of empirical data based on the analysis of generated aerosol and carried out calculations that allowed us to assess the concentrations of HPHCs in smoking products as objectively as possible. This suggests the necessity for studies that simultaneously analyze emissions from all three smoking products. In this study, we focused on comparing only those HPHCs that the WHO and the FDA specifically recommend reducing in tobacco products. These include compounds commonly found in both traditional cigarettes and alternative products. However, we did not include substances that are unique to E-cigs—such as flavoring agents, solvents like propylene glycol and glycerol, or other potentially harmful VOCs. However, our study contributes to evidence-based rather than emotion-based claims about the concept of harm reduction through the use of alternative tobacco products. The ultimate goal is to reduce the damage smoking causes to the health of smokers who cannot quit [9,10] and a reduction in the emissions of HPHCs is the first step towards reduced harm.

5. Conclusions

Based on our analysis of data from independent studies, both heated tobacco product aerosols and e-cigarette vapor contain significantly lower levels of toxicants—specifically those identified for reduction by the FDA and WHO—compared to combustible cigarette smoke, by approximately 91% and 98%, respectively. Although alternative products are not free of harmful and potentially harmful constituents, the observed reduction in emission levels suggests a substantially lower exposure to toxic substances for subjects who cannot quit. It is generally accepted that reduced exposure to toxicants is likely to correspond to reduced health risks. Therefore, our findings provide a basis for future research into the potential health effects of switching from traditional cigarettes to non-combustible alternatives. In any case, adequately designed studies are needed to assess the long-term effects of these products.

Author Contributions

Conceptualization, S.S. and N.I.; methodology, L.Z.; formal analysis, L.Z.; writing—original draft preparation, S.S.; writing—review and editing, J.Š. and N.I.; visualization, S.S. and L.Z.; supervision, N.I. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The original contributions presented in this study are included in the article. Further inquiries can be directed to the corresponding author.

Conflicts of Interest

The authors declare no conflicts of interest.

Abbreviations

The following abbreviations are used in this manuscript:
CCCombustible cigarettes
E-cigsElectronic cigarettes
HPHCsHarmful and potentially harmful constituents
HTPsHeated tobacco products
VOCsVolatile organic compounds

References

  1. Tobacco. Available online: https://www.who.int/news-room/fact-sheets/detail/tobacco (accessed on 9 June 2025).
  2. Dai, X.; Gakidou, E.; Lopez, A.D. Evolution of the Global Smoking Epidemic over the Past Half Century: Strengthening the Evidence Base for Policy Action. Tob. Control 2022, 31, 129–137. [Google Scholar] [CrossRef] [PubMed]
  3. Attitudes of Europeans towards Tobacco and Related Products—Birželis 2024—Eurobarometer Survey. Available online: https://europa.eu/eurobarometer/surveys/detail/2995 (accessed on 29 March 2025).
  4. Effects of Smoking and Tobacco|Australian Government Department of Health and Aged Care. Available online: https://www.health.gov.au/topics/smoking-vaping-and-tobacco/about-smoking/effects (accessed on 4 August 2024).
  5. St Claire, S.; Fayokun, R.; Commar, A.; Schotte, K.; Prasad, V.M. The World Health Organization’s World No Tobacco Day 2020 Campaign Exposes Tobacco and Related Industry Tactics to Manipulate Children and Young People and Hook a New Generation of Users. J. Adolesc. Heal. 2020, 67, 334. [Google Scholar] [CrossRef] [PubMed]
  6. Saint-André, V.; Charbit, B.; Biton, A.; Rouilly, V.; Possémé, C.; Bertrand, A.; Rotival, M.; Bergstedt, J.; Patin, E.; Albert, M.L.; et al. Smoking Changes Adaptive Immunity with Persistent Effects. Nature 2024, 626, 827–835. [Google Scholar] [CrossRef]
  7. The Effects of Tobacco Use on Health the Toxins in Tobacco. 2014. Available online: https://www.who.int/europe/news-room/fact-sheets/item/effects-of-tobacco-on-health (accessed on 5 May 2025).
  8. Is Nicotine Addictive?|National Institute on Drug Abuse (NIDA). Available online: https://nida.nih.gov/publications/research-reports/tobacco-nicotine-e-cigarettes/nicotine-addictive (accessed on 4 August 2024).
  9. O’Connor, R.J. Non-Cigarette Tobacco Products: What Have We Learned and Where Are We Headed? Tob. Control 2012, 21, 181. [Google Scholar] [CrossRef] [PubMed]
  10. Giebe, S.; Hofmann, A.; Brux, M.; Lowe, F.; Breheny, D.; Morawietz, H.; Brunssen, C. Comparative Study of the Effects of Cigarette Smoke versus next Generation Tobacco and Nicotine Product Extracts on Endothelial Function. Redox Biol. 2021, 47, 102150. [Google Scholar] [CrossRef] [PubMed]
  11. Lietzmann, J.; Moulac, M. Novel Tobacco and Nicotine Products and Their Effects on Health; Policy Department for Economic, Scientific and Quality of Life Policies Directorate-General for Internal Policies, European Parliament: Luxembourg, 2023. [Google Scholar]
  12. E-Cigarettes, Vapes, and Other Electronic Nicotine Delivery Systems (ENDS)|FDA. Available online: https://www.fda.gov/tobacco-products/products-ingredients-components/e-cigarettes-vapes-and-other-electronic-nicotine-delivery-systems-ends (accessed on 4 August 2024).
  13. Eaton, D.; Jakaj, B.; Forster, M.; Nicol, J.; Mavropoulou, E.; Scott, K.; Liu, C.; McAdam, K.; Murphy, J.; Proctor, C.J. Assessment of Tobacco Heating Product THP1.0. Part 2: Product Design, Operation and Thermophysical Characterisation. Regul. Toxicol. Pharmacol. 2018, 93, 4–13. [Google Scholar] [CrossRef]
  14. Mitova, M.I.; Campelos, P.B.; Goujon-Ginglinger, C.G.; Maeder, S.; Mottier, N.; Rouget, E.G.R.; Tharin, M.; Tricker, A.R. Comparison of the Impact of the Tobacco Heating System 2.2 and a Cigarette on Indoor Air Quality. Regul. Toxicol. Pharmacol. 2016, 80, 91–101. [Google Scholar] [CrossRef]
  15. Schaller, J.P.; Keller, D.; Poget, L.; Pratte, P.; Kaelin, E.; McHugh, D.; Cudazzo, G.; Smart, D.; Tricker, A.R.; Gautier, L.; et al. Evaluation of the Tobacco Heating System 2.2. Part 2: Chemical Composition, Genotoxicity, Cytotoxicity, and Physical Properties of the Aerosol. Regul. Toxicol. Pharmacol. 2016, 81, S27–S47. [Google Scholar] [CrossRef]
  16. Forster, M.; Fiebelkorn, S.; Yurteri, C.; Mariner, D.; Liu, C.; Wright, C.; McAdam, K.; Murphy, J.; Proctor, C. Assessment of Novel Tobacco Heating Product THP1.0. Part 3: Comprehensive Chemical Characterisation of Harmful and Potentially Harmful Aerosol Emissions. Regul. Toxicol. Pharmacol. 2018, 93, 14–33. [Google Scholar] [CrossRef]
  17. Chemicals in Cigarettes: From Plant to Product to Puff|FDA. Available online: https://www.fda.gov/tobacco-products/products-ingredients-components/chemicals-cigarettes-plant-product-puff (accessed on 1 May 2025).
  18. Rodgman, A.; Perfetti, T.A. The Chemical Components of Tobacco and Tobacco Smoke; CRC Press: Boca Raton, FL, USA, 2012; pp. 1–1785. [Google Scholar] [CrossRef]
  19. Holme, J.A.; Vondráček, J.; Machala, M.; Lagadic-Gossmann, D.; Vogel, C.F.A.; Le Ferrec, E.; Sparfel, L.; Øvrevik, J. Lung Cancer Associated with Combustion Particles and Fine Particulate Matter (PM2.5)—The Roles of Polycyclic Aromatic Hydrocarbons (PAHs) and the Aryl Hydrocarbon Receptor (AhR). Biochem. Pharmacol. 2023, 216, 115801. [Google Scholar] [CrossRef]
  20. Odinga, E.S.; Gudda, F.O.; Waigi, M.G.; Wang, J.; Gao, Y. Occurrence, Formation and Environmental Fate of Polycyclic Aromatic Hydrocarbons in Biochars. Fundam. Res. 2021, 1, 296–305. [Google Scholar] [CrossRef]
  21. Tane, E.G.; Martínez-Gómez, L.; Amorós-Pérez, A.; Román-Martínez, M.C.; Lillo-Ródenas, M.A. A Novel Approach to the Quantitative Analysis of the Particulate Matter in Conventional Cigarette Smoke and Heated Tobacco Product Aerosols. Heliyon 2024, 10, e35028. [Google Scholar] [CrossRef] [PubMed]
  22. World Health Organization. Heated Tobacco Products: Summary of Research and Evidence of Health Impacts; World Health Organization: Geneva, Switzerland, 2023; ISBN 9789240042490. [Google Scholar]
  23. Vukas, J.; Mallock-Ohnesorg, N.; Rüther, T.; Pieper, E.; Romano-Brandt, L.; Stoll, Y.; Hoehne, L.; Burgmann, N.; Laux, P.; Luch, A.; et al. Two Different Heated Tobacco Products vs. Cigarettes: Comparison of Nicotine Delivery and Subjective Effects in Experienced Users. Toxics 2023, 11, 525. [Google Scholar] [CrossRef]
  24. Kaisar, M.A.; Prasad, S.; Liles, T.; Cucullo, L. A Decade of E-Cigarettes: Limited Research & Unresolved Safety Concerns. Toxicology 2016, 365, 67–75. [Google Scholar] [CrossRef] [PubMed]
  25. Travis, N.; Knoll, M.; Cook, S.; Oh, H.; Cadham, C.J.; Sánchez-Romero, L.M.; Levy, D.T. Chemical Profiles and Toxicity of Electronic Cigarettes: An Umbrella Review and Methodological Considerations. Int. J. Environ. Res. Public Health 2023, 20, 1908. [Google Scholar] [CrossRef]
  26. Heywood, J.; Abele, G.; Langenbach, B.; Litvin, S.; Smallets, S.; Paustenbach, D. Composition of E-Cigarette Aerosols: A Review and Risk Assessment of Selected Compounds. J. Appl. Toxicol. 2024, 45, 364–386. [Google Scholar] [CrossRef]
  27. Harmful and Potentially Harmful Constituents in Tobacco Products and Tobacco Smoke: Established List|FDA. Available online: https://www.fda.gov/tobacco-products/rules-regulations-and-guidance-related-tobacco-products/harmful-and-potentially-harmful-constituents-tobacco-products-and-tobacco-smoke-established-list (accessed on 16 March 2025).
  28. Burns, D.M.; Dybing, E.; Gray, N.; Hecht, S.; Anderson, C.; Sanner, T.; O’Connor, R.; Djordjevic, M.; Dresler, C.; Hainaut, P.; et al. Mandated Lowering of Toxicants in Cigarette Smoke: A Description of the World Health Organization TobReg Proposal. Tob. Control 2008, 17, 132–141. [Google Scholar] [CrossRef]
  29. World Health Organization. The Scientific Basis of Tobacco Product Regulation; World Health Organization: Geneva, Switzerland, 2009; pp. 1–287. [Google Scholar]
  30. CTRP. 3R4F Composition: Preliminary Analysis. Available online: https://ctrp.uky.edu/products/gallery/Reference%20Cigarettes/detail/936 (accessed on 19 May 2025).
  31. Sansone, L.; Milani, F.; Fabrizi, R.; Belli, M.; Cristina, M.; Zagà, V.; de Iure, A.; Cicconi, L.; Bonassi, S.; Russo, P. Nicotine: From Discovery to Biological Effects. Int. J. Mol. Sci. 2023, 24, 14570. [Google Scholar] [CrossRef]
  32. Münzel, T.; Hahad, O.; Kuntic, M.; Keaney, J.F.; Deanfield, J.E.; Daiber, A. Effects of Tobacco Cigarettes, e-Cigarettes, and Waterpipe Smoking on Endothelial Function and Clinical Outcomes. Eur. Heart J. 2020, 41, 4057. [Google Scholar] [CrossRef]
  33. Bekki, K.; Inaba, Y.; Uchiyama, S.; Kunugita, N. Comparison of Chemicals in Mainstream Smoke in Heat-Not-Burn Tobacco and Combustion Cigarettes. J. UOEH 2017, 39, 201–207. [Google Scholar] [CrossRef]
  34. Mallock, N.; Böss, L.; Burk, R.; Danziger, M.; Welsch, T.; Hahn, H.; Trieu, H.L.; Hahn, J.; Pieper, E.; Henkler-Stephani, F.; et al. Levels of Selected Analytes in the Emissions of “Heat Not Burn” Tobacco Products That Are Relevant to Assess Human Health Risks. Arch. Toxicol. 2018, 92, 2145–2149. [Google Scholar] [CrossRef]
  35. Li, X.; Luo, Y.; Jiang, X.; Zhang, H.; Zhu, F.; Hu, S.; Hou, H.; Hu, Q.; Pang, Y. Chemical Analysis and Simulated Pyrolysis of Tobacco Heating System 2.2 Compared to Conventional Cigarettes. Nicotine Tob. Res. 2019, 21, 111–118. [Google Scholar] [CrossRef] [PubMed]
  36. Wang, H.; Chen, H.; Huang, L.; Li, X.; Wang, L.; Li, S.; Liu, M.; Zhang, M.; Han, S.; Jiang, X.; et al. In Vitro Toxicological Evaluation of a Tobacco Heating Product THP COO and 3R4F Research Reference Cigarette on Human Lung Cancer Cells. Toxicol. Vitr. 2021, 74, 105173. [Google Scholar] [CrossRef]
  37. Grech, A.K.; Keating, D.T.; Garner, D.J.; Naughton, M.T. A Case of Extreme Carboxyhaemoglominemia Due to Vaping. Respirol. Case Rep. 2022, 10, e0942. [Google Scholar] [CrossRef] [PubMed]
  38. Pinto, M.I.; Thissen, J.; Hermes, N.; Cunningham, A.; Digard, H.; Murphy, J. Chemical Characterisation of the Vapour Emitted by an E-Cigarette Using a Ceramic Wick-Based Technology. Sci. Rep. 2022, 12, 16497. [Google Scholar] [CrossRef] [PubMed]
  39. Lu, F.; Yu, M.; Chen, C.; Liu, L.; Zhao, P.; Shen, B.; Sun, R. The Emission of VOCs and CO from Heated Tobacco Products, Electronic Cigarettes, and Conventional Cigarettes, and Their Health Risk. Toxics 2022, 10, 8. [Google Scholar] [CrossRef]
  40. Leigh, N.J.; Palumbo, M.N.; Marino, A.M.; O’Connor, R.J.; Goniewicz, M.L. Tobacco-Specific Nitrosamines (TSNA) in Heated Tobacco Product IQOS. Tob. Control 2018, 27, s37–s38. [Google Scholar] [CrossRef]
  41. Olasehinde, T.A.; Olaniran, A.O. Neurotoxicity of Anthracene and Benz[a]Anthracene Involves Oxidative Stress-Induced Neuronal Damage, Cholinergic Dysfunction and Disruption of Monoaminergic and Purinergic Enzymes. Toxicol. Res. 2022, 38, 365–377. [Google Scholar] [CrossRef]
  42. Adesina, O.A.; Olowolafe, T.I.; Igbafe, A. Levels of Polycyclic Aromatic Hydrocarbon from Mainstream Smoke of Tobacco Products and Its Risks Assessment. J. Hazard. Mater. Adv. 2022, 5, 100053. [Google Scholar] [CrossRef]
  43. Uchiyama, S.; Noguchi, M.; Takagi, N.; Hayashida, H.; Inaba, Y.; Ogura, H.; Kunugita, N. Simple Determination of Gaseous and Particulate Compounds Generated from Heated Tobacco Products. Chem. Res. Toxicol. 2018, 31, 585–593. [Google Scholar] [CrossRef]
  44. Xu, Y.; Williams, S.J.; O’brien, D.; Davidge, S.T.; Xu, Y.; Williams, S.J.; O’brien, D.; Davidge, S.T. Polycyclic Aromatic Hydrocarbons. FASEB J. 2010, 20, 1251–1253. [Google Scholar] [CrossRef] [PubMed]
  45. Vu, A.T.; Taylor, K.M.; Holman, M.R.; Ding, Y.S.; Hearn, B.; Watson, C.H. Polycyclic Aromatic Hydrocarbons in the Mainstream Smoke of Popular U.S. Cigarettes. Chem. Res. Toxicol. 2015, 28, 1616. [Google Scholar] [CrossRef] [PubMed]
  46. Simonavicius, E.; McNeill, A.; Shahab, L.; Brose, L.S. Heat-Not-Burn Tobacco Products: A Systematic Literature Review. Tob. Control 2019, 28, 582–594. [Google Scholar] [CrossRef]
  47. Goniewicz, M.L.; Knysak, J.; Gawron, M. Levels of Selected Carcinogens and Toxicants in Vapour from Electronic Cigarettes. Tob. Control 2014, 23, 133–139. [Google Scholar] [CrossRef]
  48. Formaldehyde and Cancer Risk|American Cancer Society. Available online: https://www.cancer.org/cancer/risk-prevention/chemicals/formaldehyde.html (accessed on 14 March 2025).
  49. Ruggiero, J.L.; Voller, L.M.; Shaik, J.A.; Hylwa, S. Formaldehyde in Electronic Cigarette Liquid (Aerosolized Liquid). Dermatitis 2022, 33, 332–336. [Google Scholar] [CrossRef]
  50. Samburova, V.; Bhattarai, C.; Strickland, M.; Darrow, L.; Angermann, J.; Son, Y.; Khlystov, A. Aldehydes in Exhaled Breath during E-Cigarette Vaping: Pilot Study Results. Toxics 2018, 6, 46. [Google Scholar] [CrossRef] [PubMed]
  51. Chen, L.; Wang, M.; Villalta, P.W.; Luo, X.; Feuer, R.; Jensen, J.; Hatsukami, D.K.; Hecht, S.S. Quantitation of an Acetaldehyde Adduct in Human Leukocyte DNA and the Effect of Smoking Cessation. Chem. Res. Toxicol. 2007, 20, 108–113. [Google Scholar] [CrossRef]
  52. Nabavizadeh, P.; Liu, J.; Rao, P.; Ibrahim, S.; Han, D.D.; Derakhshandeh, R.; Qiu, H.; Wang, X.; Glantz, S.A.; Schick, S.F.; et al. Impairment of Endothelial Function by Cigarette Smoke Is Not Caused by a Specific Smoke Constituent, but by Vagal Input from the Airway. Arter. Thromb. Vasc. Biol. 2022, 42, 1324. [Google Scholar] [CrossRef]
  53. Srivastava, S.; Sithu, S.D.; Vladykovskaya, E.; Haberzettl, P.; Hoetker, D.J.; Siddiqui, M.A.; Conklin, D.J.; D’Souza, S.E.; Bhatnagar, A. Oral Exposure to Acrolein Exacerbates Atherosclerosis in Apo E-Null Mice. Atherosclerosis 2011, 215, 301. [Google Scholar] [CrossRef]
  54. Sithu, S.D.; Srivastava, S.; Siddiqui, M.A.; Vladykovskaya, E.; Riggs, D.W.; Conklin, D.J.; Haberzettl, P.; O’Toole, T.E.; Bhatnagar, A.; D’Souza, S.E. Exposure to Acrolein by Inhalation Causes Platelet Activation. Toxicol. Appl. Pharmacol. 2010, 248, 100–110. [Google Scholar] [CrossRef]
  55. DeJarnett, N.; Yeager, R.; Conklin, D.J.; Lee, J.; O’Toole, T.E.; McCracken, J.; Abplanalp, W.; Srivastava, S.; Riggs, D.W.; Hamzeh, I.; et al. Residential Proximity to Major Roadways Is Associated with Increased Levels of AC133+ Circulating Angiogenic Cells. Arter. Thromb. Vasc. Biol. 2015, 35, 2468–2477. [Google Scholar] [CrossRef] [PubMed]
  56. Conklin, D.J.; Barski, O.A.; Lesgards, J.F.; Juvan, P.; Rezen, T.; Rozman, D.; Prough, R.A.; Vladykovskaya, E.; Liu, S.Q.; Srivastava, S.; et al. Acrolein Consumption Induces Systemic Dyslipidemia and Lipoprotein Modification. Toxicol. Appl. Pharmacol. 2010, 243, 1–12. [Google Scholar] [CrossRef] [PubMed]
  57. ICSC. 0550—Propionaldehyde. Available online: https://chemicalsafety.ilo.org/dyn/icsc/showcard.display?p_card_id=0550 (accessed on 17 March 2025).
  58. Xie, M.Z.; Liu, J.L.; Gao, Q.Z.; Bo, D.Y.; Wang, L.; Zhou, X.C.; Zhao, M.M.; Zhang, Y.C.; Zhang, Y.J.; Zhao, G.A.; et al. Proteomics-Based Evaluation of the Mechanism Underlying Vascular Injury via DNA Interstrand Crosslinks, Glutathione Perturbation, Mitogen-Activated Protein Kinase, and Wnt and ErbB Signaling Pathways Induced by Crotonaldehyde. Clin. Proteom. 2022, 19, 33. [Google Scholar] [CrossRef]
  59. Jin, L.; Jagatheesan, G.; Lynch, J.; Guo, L.; Conklin, D.J. Crotonaldehyde-Induced Vascular Relaxation and Toxicity: Role of Endothelium and Transient Receptor Potential Ankyrin-1 (TRPA1). Toxicol. Appl. Pharmacol. 2020, 398, 115012. [Google Scholar] [CrossRef]
  60. Pauwels, C.G.G.M.; Klerx, W.N.M.; Pennings, J.L.A.; Boots, A.W.; Van Schooten, F.J.; Opperhuizen, A.; Talhout, R. Cigarette Filter Ventilation and Smoking Protocol Influence Aldehyde Smoke Yields. Chem. Res. Toxicol. 2018, 31, 462–471. [Google Scholar] [CrossRef] [PubMed]
  61. Farsalinos, K.E.; Yannovits, N.; Sarri, T.; Voudris, V.; Poulas, K.; Leischow, S.J. Carbonyl Emissions from a Novel Heated Tobacco Product (IQOS): Comparison with an e-Cigarette and a Tobacco Cigarette. Addiction 2018, 113, 2099–2106. [Google Scholar] [CrossRef]
  62. Health Effects—Toxicological Profile for Toluene—NCBI Bookshelf. Available online: https://www.ncbi.nlm.nih.gov/books/NBK592498/ (accessed on 14 March 2025).
  63. Abplanalp, W.; DeJarnett, N.; Riggs, D.W.; Conklin, D.J.; McCracken, J.P.; Srivastava, S.; Xie, Z.; Rai, S.; Bhatnagar, A.; O’Toole, T.E. Benzene Exposure Is Associated with Cardiovascular Disease Risk. PLoS ONE 2017, 12, e0183602. [Google Scholar] [CrossRef]
  64. Ong, C.N.; Lee, B.L.; Shi, C.Y.; Ong, H.Y.; Lee, H.P. Elevated Levels of Benzene-Related Compounds in the Urine of Cigarette Smokers. Int. J. Cancer 1994, 59, 177–180. [Google Scholar] [CrossRef]
  65. Korte, J.E.; Hertz-Picciotto, I.; Schulz, M.R.; Ball, L.M.; Duell, E.J. The Contribution of Benzene to Smoking-Induced Leukemia. Environ. Health Perspect. 2000, 108, 333. [Google Scholar] [CrossRef]
  66. Casalegno, C.; Schifanella, O.; Zennaro, E.; Marroncelli, S.; Briant, R. Collate Literature Data on Toxicity of Chromium (Cr) and Nickel (Ni) in Experimental Animals and Humans. EFSA Support. Publ. 2015, 12, 478E. [Google Scholar] [CrossRef]
  67. Haleem, A.M.; Amin, S.; Mahmood, U.H. Heavy Metal and Polycyclic Aromatic Hydrocarbons in Cigarettes: An Analytical Assessment. Popul. Med. 2020, 2, 19. [Google Scholar] [CrossRef]
  68. Cadmium—Health Effects|Occupational Safety and Health Administration. Available online: https://www.osha.gov/cadmium/health-effects (accessed on 17 March 2025).
  69. 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. PLoS ONE 2013, 8, e57987. [Google Scholar] [CrossRef] [PubMed]
  70. Ashraf, M.W. Levels of Heavy Metals in Popular Cigarette Brands and Exposure to These Metals via Smoking. Sci. World J. 2012, 2012, 729430. [Google Scholar] [CrossRef] [PubMed]
  71. Cohen, J.T.; Bellinger, D.C.; Shaywitz, B.A. A Quantitative Analysis of Prenatal Methyl Mercury Exposure and Cognitive Development. Am. J. Prev. Med. 2005, 29, 353. [Google Scholar] [CrossRef]
  72. Son, Y.; Bhattarai, C.; Samburova, V.; Khlystov, A. Carbonyls and Carbon Monoxide Emissions from Electronic Cigarettes Affected by Device Type and Use Patterns. Int. J. Environ. Res. Public. Health 2020, 17, 2767. [Google Scholar] [CrossRef]
  73. Lechasseur, A.; Morissette, M.C. The Fog, the Attractive and the Addictive: Pulmonary Effects of Vaping with a Focus on the Contribution of Each Major Vaping Liquid Constituent. Eur. Respir. Rev. 2020, 29, 200268. [Google Scholar] [CrossRef]
  74. Komura, M.; Sato, T.; Yoshikawa, H.; Nitta, N.A.; Suzuki, Y.; Koike, K.; Kodama, Y.; Seyama, K.; Takahashi, K. Propylene Glycol, a Component of Electronic Cigarette Liquid, Damages Epithelial Cells in Human Small Airways. Respir. Res. 2022, 23, 216. [Google Scholar] [CrossRef]
  75. Eaton DL, K.L.; Stratton, K. (Eds.) Public Health Consequences of E-Cigarettes; National Academies Press: Washington, DC, USA, 2018. [Google Scholar] [CrossRef]
  76. Strongin, R.M. E-Cigarette Chemistry and Analytical Detection. Annu. Rev. Anal. Chem. 2019, 12, 23–39. [Google Scholar] [CrossRef]
  77. Sassano, M.F.; Davis, E.S.; Keating, J.E.; Zorn, B.T.; Kochar, T.K.; Wolfgang, M.C.; Glish, G.L.; Tarran, R. Evaluation of E-Liquid Toxicity Using an Open-Source High-Throughput Screening Assay. PLoS Biol. 2018, 16, e2003904. [Google Scholar] [CrossRef]
Figure 1. The reduction (%) in HPHCs between combustible cigarettes and alternative products: (a) heated tobacco products (HTPs) and (b) e-cigarettes (E-cigs). The percentage of reductions were calculated in comparison with 3R4F.
Figure 1. The reduction (%) in HPHCs between combustible cigarettes and alternative products: (a) heated tobacco products (HTPs) and (b) e-cigarettes (E-cigs). The percentage of reductions were calculated in comparison with 3R4F.
Ijerph 22 01010 g001
Table 1. Table summarizing the median concentrations of the determined HPHCs per single puff.
Table 1. Table summarizing the median concentrations of the determined HPHCs per single puff.
CompoundHarm CausedConcentration per 1 Puff
Median [Min–Max]
References
3R4FHeated Tobacco ProductsElectronic Cigarettes
Nicotine, mgCauses addiction, has inflammatory and anti-inflammatory properties [31]. 0.17
[0.09–0.22]
0.1
[0.09–0.11]
0.05
[0.02–0.32]
[32,33,34,35,36]
Carbon monoxide, mgIs associated with chronic carboxyhaemoglobinemia and the development of cardiorespiratory disease [37].2.78
[1.32–3.7]
0.04
[0.03–0.06]
0.002
[0.001–0.003]
[33,35,36,38,39,40]
Polycyclic aromatic Hydrocarbons (PAH)
Benz[a]anthraceneOxidative stress inducer leading neuronal damage [41].2.84
[2.47–3.21]
0.13
[0.12–0.22]
<LOD[38,40,42,43]
Benzo[b+k]fluoranthene, ngCarcinogen [44].0.62
[0.4–0.83]
0.03
[0.01–0.04]
0.016
[0.01–0.018]
[38,40,42,43]
Benzo[a]pyrene, ngThe most potent carcinogen among polycyclic aromatic hydrocarbons [45].1.40
[0.69–1.67]
0.05
[0.04–0.06]
0.003
[0.002–0.006]
[38,40,42,43]
Tobacco-specific Nitrosamines
N′-nitrosonornicotine (NNN), ngCarcinogen [46].24.68
[12.89–34.57]
0.96
[0.87–1.75]
-
[<LOD–0.002]
[32,33,35,36,38,47]
N′-nitrosoanabasine (NAB), ngCarcinogen [46].2.67
[1.6–3.64]
0.26
[0.2–0.47]
-
<LOD
[32,33,35,36,38,47]
4-(Methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK), ngCarcinogen [46].22.25
[14.3–27.82]
0.61
[0.2–0.88]
-
[<LOD–0.004]
[32,33,35,36,38,47]
N′-nitrosoanatabine (NAT), ng Carcinogen [46].20.98
[14.3–27.82]
1.51
[1.23–1.75]
-
[<LOD–0.005]
[32,33,35,36,38,47]
Carbonyls
Formaldehyde, μgCarcinogen [48], has a toxic effect at the cellular level. Causes irritation of the airways and damage to airway cells, a source of contact dermatitis [49].4.7
[1.88–8.09]
0.53 [0.11–1.9] 0.04
[0.03–0.12]
[32,34,35,36,43,47,50]
Acetaldehyde, μgOne of the most common carcinogens in cigarette smoke [51]. 127.1 [136.4–154] 16.5
[9.5–18.26]
0.01
[0.01–0.1]
[32,34,35,36,43,47,50]
Acroleine, μgPromotes endothelial dysfunction, oxidative stress, dyslipidemia, and platelet activation [52]. Chronic exposure to acrolein through cigarette smoke has been associated with asthma, acute lung damage, chronic obstructive pulmonary disease (COPD), and respiratory cancer [53,54,55,56]. 12.37 [11.82–16.22] 0.67 [0.04–0.94] 0.06
[0.003–0.17]
[32,34,35,36,43,47,50]
Propionaldehyde, μgCauses cough and sore throat [57].10.67
[6.2–13.02]
1.07
[0.56–1.61]
-
[<LOD–0.002]
[32,34,35,36,43,47,50]
Crotonaldehyde, μgA potent eye, respiratory, and skin irritant, associated with cardiopulmonary toxicity and cardiovascular disease [56,58,59]. 4.36
[1.29–4.7]
0.4
[0.05–0.83]
-
[<LOD–0.001]
[35,36,47,60,61]
Volatile organic compounds
Toluene μgNegatively affects the brain and central nervous system [62]14.89
[10.38–21.41]
0.14
[0.12–0.22]
-
[<LOD–0.003]
[34,35,36,38,43]
Benzene, μgIncreases the risk of leukemia, lymphoma, and cardiovascular disease. Causes a deficiency of circulating angiogenic cells and increases low-density lipoprotein levels [63,64,65].7.91
[6.62–10]
0.05
[0.04–0.08]
-
[<LOD–0.0008]
[34,35,36,38,43]
Inorganic compounds
Nickel, ngGenotoxic effects, may increase the risk of oral cancer [66].0.41
[0.39–1.43]
<LOD0.0015
[0.001–0.002]
[35,36,47,61,67]
Cadmium, ngAcute inhalation exposure may result in flu-like symptoms and may damage the lungs. Chronic exposure can result in kidney, bone, and lung disease [68].11.87
[8.54–15.2]
-
<LOD
-
<LOD
[35,36,47,61,67]
Chromium, ngInhalation may cause respiratory irritation [69].0.09
[0.09–0.19]
<LOD<LOD[35,36,47,61,67]
Lead, ng Causes oxidative stress in cells, may cause lung cancer, has a strong negative effect on the brain, nervous system and red blood cells [70].3.26
[2.9–3.62]
-
[<LOD–0.76]
-
[<LOD-003]
[35,36,47,61,67]
Mercury, ngMay have toxic effects on the nervous, digestive, and immune systems, and on lungs, kidneys, skin, and eyes [71]. 0.42
[0.25–0.48]
<LOD <LOD[35,36,47,61,67]
LOD—below limit of detection.
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Sakalauskaite, S.; Zdanavicius, L.; Šteinmiller, J.; Istomina, N. Exposure to Toxic Compounds Using Alternative Smoking Products: Analysis of Empirical Data. Int. J. Environ. Res. Public Health 2025, 22, 1010. https://doi.org/10.3390/ijerph22071010

AMA Style

Sakalauskaite S, Zdanavicius L, Šteinmiller J, Istomina N. Exposure to Toxic Compounds Using Alternative Smoking Products: Analysis of Empirical Data. International Journal of Environmental Research and Public Health. 2025; 22(7):1010. https://doi.org/10.3390/ijerph22071010

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Sakalauskaite, Sandra, Linas Zdanavicius, Jekaterina Šteinmiller, and Natalja Istomina. 2025. "Exposure to Toxic Compounds Using Alternative Smoking Products: Analysis of Empirical Data" International Journal of Environmental Research and Public Health 22, no. 7: 1010. https://doi.org/10.3390/ijerph22071010

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Sakalauskaite, S., Zdanavicius, L., Šteinmiller, J., & Istomina, N. (2025). Exposure to Toxic Compounds Using Alternative Smoking Products: Analysis of Empirical Data. International Journal of Environmental Research and Public Health, 22(7), 1010. https://doi.org/10.3390/ijerph22071010

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