Open Access Article
This Open Access Article is licensed under a Creative Commons Attribution-Non Commercial 3.0 Unported Licence

The chemical memory of smoking tobacco

D. Gallart-Mateu a, P. Dualde b, C. Coscollà b, J. M. Soriano c and M. de la Guardia *a
aDepartment of Analytical Chemistry, University of Valencia, Research Building, 50 Dr Moliner Street, 16100-Burjassot, Valencia, Spain. E-mail: daniel.gallart@uv.es; Miguel.delaguadia@uv.es; Tel: +34 963 544 838
bFoundation for the Promotion of Health and Biomedical Research in the Valencian Region, FISABIO-Public Health, Av. Catalunya, 21, Valencia, 46020, Spain
cGISP Grup d’Investigació en Salut Pública, Universitat Politècnica de Catalunya, Spain

Received 11th March 2024 , Accepted 2nd May 2024

First published on 20th May 2024


Abstract

The concentration in urine of N-acetyl-hydroxy-propyl-cisteine (3HPMA), an acrolein metabolite, has been employed as a marker of the risk of illness of smokers and the relative concentration of creatinine has been evaluated to verify the effect of moving from the practice of burning tobacco to nicotine vaping. From the results concerning the urine samples of 38 subjects, collected from 2021 to 2023 and analyzed by LC-MS/MS, corresponding to 5 active smokers, 13 previously heavy smokers who replaced traditional tobacco by vaping, and 20 non-smokers, a dramatic reduction was found in 3HPMA/creatinine in urine. 3HPMA varied from values of 2150–3100 μg gcreatinine−1 to levels of 225–625 μg gcreatinine−1 found for non-smokers, with the time decay described by the equation y = 0.3661x2 − 94.359x + 6246.4 (R2: 0.757), providing a time of approximately 10 years for tobacco memory after the cessation of the consumption of burned tobacco.


Introduction

The practice of smoking damages every organ in the body, making tobacco smoking one of the most important causes of premature death around the world.1 According to the World Health Organization (WHO), tobacco consumption causes the deaths of millions of people annually, with a higher death rate than other diseases such as human immunodeficiency virus (HIV), tuberculosis and malaria combined.2

Tobacco smoking is mainly related to several health problems, such as cancer, and cardiovascular and respiratory diseases. In this sense, smoking practices are associated with processes of inflammation and oxidative stress, related to the pathophysiology of these aforementioned diseases.3,4 Since 2009, several national and international agencies have been involved in the monitoring and control of tobacco products.5 In 2017, the United States Food and Drugs Administration (FDA) published a list of 20 harmful and potentially harmful constituents (HPHCs) of tobacco and tobacco smoke, including nicotine and other alkaloids, carbon monoxide, tobacco-specific nitrosamines (TSNAs), polycyclic aromatic hydrocarbons (PAHs), volatile organic compounds (VOCs), carcinogenic aromatic amines, and mineral ions, and the list is still current today.6 The biomarkers related to the aforementioned processes, derived from precursors included in the FDA HPHC list, are very useful for monitoring the diseases related to tobacco smoking, particularly in their first stages.7Table 1 indicates some of the most common HPHCs present in tobacco smoke and their metabolites in the human body together with diseases related to tobacco smoking and the usual matrices in which they are monitored.8

Table 1 HPHCs, metabolites, pathologies and the usual matrix employed in the monitoring of diseases related to tobacco consumption8
Parent Metabolite Usual matrix Developed pathology
1,3-Butadiene Monohydroxybutenyl mercapturic acid (MHBMA) Urine Cancer
Respiratory disease
Reproductive toxicant
2-Aminonapthalene 2-Aminonapthalene (2-AN) Cancer
4-Aminobiphenyl 4-Aminobiphenyl (4-ABP) Cancer
o-Toluidine o-Toluidine (o-T) Cancer
Acrolein 3-Hydroxypropyl mercapturic acid (3-HPMA) Respiratory disease
Cardiovascular disease
Benzene S-phenyl mercapturic acid (SPMA) Cancer
Cardiovascular disease
Reproductive toxicant
Respiratory disease
Ethylene oxide 2-Hydroxyethyl mercapturic acid (HEMA) Cancer
Respiratory disease
Reproductive toxicant
Hydrogen cyanide Thiocyanate (SCN) Respiratory disease
Cardiovascular disease
4-(Methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK) 4-(Methylnitrosamino)-1-(3-pyridyl)-1-butanol and related glucoronides (total NNAL) Cancer
Carbon monoxide Carboxyhemoglobin (COHb) Blood Reproductive toxicant
Cardiovascular disease


Several studies have been published concerning the concentration of HPHC metabolites in biological fluids from smokers, former smokers who had substituted traditional practices by harm-reduction alternatives, and smokers who had ceased their smoking activities completely. In this sense, Gale et al. in 2021,9 monitored the concentration in urine of total-NNAL, total-NNN, 3HPMA, HMPMA, MHBMA, HEMA, 4-ABP or CEMA. A comparison between two different population sets, current smokers and people who had substituted traditional tobacco by alternative products, showed that while the concentrations of biomarkers in the urine of current smokers remained practically constant throughout the whole study time, in the case of people using alternative products, the studied biomarkers decreased from the initial time until the end and finally remained practically constant. The same authors performed a one-year study by comparing HPHC metabolites in four different population groups: (i) current smokers, (ii) people who has substituted traditional tobacco by alternative products, (iii) people who had completely ceased traditional tobacco consumption, and (iv) non-smokers.10 From this study, it could be concluded that the concentration in current smokers remained constant throughout the time, while the presence of biomarkers in urine decreased substantially when traditional tobacco consumption was substituted or completely avoided.

In a previous study,11 we evaluated exposure to tobacco and nicotine vaping through the urine control of six metabolites of acrylonitrile, acrolein and crotonaldehyde in urine samples of active traditional smokers, past strong smokers who moved to vaping, and non-smokers, which confirmed that N-acetyl-S-(2-cyanoethyl)-L-cysteine (CEMA) is present only in active smokers and that levels of 2R-N-acetyl-S-(4-hydroxybutan-2-yl)-L-cysteine (HMPMA) and N-acetyl-S-[1-(hydroxymethyl)-2-propen-1-yl)]-L-cysteine (MHBMA) in vapers' urine are at the same level of magnitude as smokers and non-smokers. The level of N-acetyl-S-(3,4-dihydroxybutyl)-L-cysteine (DHBMA) in the urine of previous smokers reached similar values to those determined in non-smokers and it was also observed that levels of N-acetyl-hydroxy-propyl-cisteine (3HPMA) in urine showed a strong reduction on moving from smoking to vaping. N-acetyl-S-(3-carboxy-2-propyl)-L-cysteine (CMEMA) in the urine of vapers can reach concentrations higher than those found in the cases of non-smokers and smokers.

In this study, the relationship was evaluated between the 3HPMA in the urine of previous smokers who moved to nicotine vaping as their single nicotine consumption practice, in order to undertake a preliminary determination based on molecular markers of the time required after consumption of burnt tobacco ceased to reduce the risk of illness.

From a medical point of view, several studies have shown the biological effect of cessation of smoking on disease risks. Jeong et al.12 found a 20% decrease in cardiovascular disease risk on cessation of smoking after one to three years. In the same way, Polosa et al.13 evidenced the harm reduction in chronic obstructive pulmonary disease (COPD) twenty-four months after cessation of traditional smoking practices and substitution by alternative practices, while Huang et al.14 and Fares et al.15 established a relationship between negative pulmonary diagnosis and smoking cessation from one to five years after stopping smoking. So, it can be concluded that there is evidence of a certain memory of tobacco smoking which must be clarified. On the other hand, specialized sources argue that heavy smokers can reduce the risk of health diseases in a period of five to ten years after cessation in spite of the risks of pulmonary diseases that are difficult to solve.16

Acrolein is considered one of cigarette smoke's most toxic and harmful components.16,17 It is involved in the development of several diseases, including multiple sclerosis, neurodegenerative diseases such as Alzheimer's disease, cardiovascular and respiratory diseases, diabetes mellitus and even the development of cancer due to its high reactivity, cytotoxicity and genotoxicity.18,19 Smokers are particularly exposed to the harmful effects of acrolein due the high concentration found in tobacco smoke. Chronic exposure to acrolein has been linked to the development of asthma, acute lung injury, chronic obstructive pulmonary disease and even respiratory cancers.20 Considering the importance of acrolein, its exposition monitoring seems to be very important for making a diagnosis, assessing disease progression, and validating treatments that specifically target acrolein. In recent years, the relevance of 3HPMA, a specific and stable metabolite of acrolein, has been demonstrated as a reliable biomarker of acrolein in urine, being very useful for biomonitoring purposes and to assess the evolution and the memory, in terms of possible disease exposition, of tobacco consumption and its cessation.21–23

Materials and methods

Reagents and standards

N-acetyl-S-(3-hydroxypropyl)-L-cysteine sodium salt (3HPMA, CAS: 14369-42-7), with a purity higher than 98%, was obtained from TLC Pharmaceutical Standards (New Market, ON, Canada). Terfenadine and Val-Tyr-Val from Sigma Life Sciences (St. Louis, MO, USA), triallyl phosphite from Alfa Aesar Thermo Fischer (Kandel, Germany) and sulfaguanidine, sulfadimethoxine, reserpine and acetaminophen obtained from Sigma-Aldrich (St. Louis, MO, USA) were employed as internal standards for LC-MS/MS in 3HPMA determination.

Methanol (LC-MS grade), acetonitrile (LC-MS quality) and buffer constituents, acetic acid and ammonium formate, were provided by VWR Chemicals (Radnor, PA, USA) and Scharlau (Barcelona, Spain). Ultrapure water with a maximum resistivity of 18.2 MΩ cm−1 from an Adrona B-30 Bio system (Adrona, Riga, Latvia) was used.

Sample population

The first morning urine samples of 38 subjects who did not suffer from renal affections, including 5 smokers, 20 non-smokers and 13 declared vapers, were collected using sterile flasks. Men and women volunteers were selected, taking into account their former smoking practice and present vaping habits. All the participants were informed of the objective of the study and a consent document including a confidentiality agreement between the University and the participants was provided and signed. The original samples and aliquots of 10 mL from the freshly received samples were frozen until their analysis.

Creatinine analysis

Creatinine was used to normalize the data of the target analyte in order to minimize the effect of the characteristics and habits of the volunteers. Creatinine determination was performed using a Linear Kroma autoanalyzer (Holliston, MA, USA). The analysis methodology is based on the colorimetric determination of creatinine using 20 μL of urine by the formation of the Janovsky complex through reaction with alkaline picrate based on the Jaffé reaction.24 The employed methodology allowed the determination of creatinine in urine samples down to concentrations of 0.01 g L−1.

Determination of 3HPMA by LC-MS/MS

The determination of 3HPMA was carried out using a Vanquish UHPLC chromatograph from Thermo Scientific (Waltham, MA, USA) with a triple quadrupole mass spectrometer TSQAltis, operated in multiple reaction mode, from Thermo Scientific (Waltham, MA, USA). A Hypersil GOLD C18 column, 1.9 μm (150 × 2.1 mm), provided by Thermo Scientific (Waltham, MA, USA), was employed using a gradient of two mobile phases, ammonium formate (5 mM) in 0.1% acetic acid in ultrapure water (A) and acetonitrile of HPLC-MS quality (B). The column temperature was 40 °C. To perform the chromatographic separation, the applied mobile phase gradient was: 99.5% A from the beginning to 0.5 minutes, then decreasing to 70% A until minute 2, maintaining 70% A until minute 7, followed to decreasing to 0% A at minute 8 and maintaining only phase B until minute 12. Finally, increasing the proportion of mobile phase A to 99.5% at minute 12.1 and maintaining this proportion until the end of the program (minute 18).

The analysis of 3HPMA was carried out using negative ionization (ESI−) by applying a voltage of 3300 V. The injections were made in cycles of 0.8 seconds and the injection volume was 10 μL. The determination of the analyte was performed using the 220m/z precursor ion, 90m/z for the quantification ion and 89m/z for the confirmation ion, with collision energies of 13.72 V and 21.51 V applied for quantification and confirmation ions, respectively.

A concentrated standard solution in water was prepared from the commercial standard. The calibration solutions were prepared in the concentration range between 9 and 750 ng mL−1, and were made by mixing 100 μL of non-smokers’ urine (urine blank), 20 μL of 8 μg mL−1 internal standard solution, and the appropriate volume of 3HPMA standard solution to reach the required concentration. Ultrapure water was added to a final volume of 1 mL. Then, 1 mL of properly diluted urine samples were spiked with 20 μL of multi-internal standard solution of an adequate concentration, and analyzed.

The precision and accuracy of analyte determination were established from three independent replicates of non-smoker urine blanks spiked at concentrations between 9 and 750 ng mL−1 and analyzed as unknown samples.

Results and discussion

Characteristics of studied population

A sampling process following the University of Valencia ethics committee guidelines, verification code X0H21EQATBAG6TVF, was performed. Table 2 indicates the characteristics of the 38 subjects included in this study, 13 male and 25 female, spanning the age range from 20 to 79 years for men and from 16 to 76 years for women. Urine samples were obtained from 13 vapers (5 male and 8 female), 5 smokers (2 male and 3 female) and 20 non-smokers (6 male and 14 female) as a control group. Vapers were former smokers who had smoked for 8–30 years and who had used vaping systems for from 84 to 132 months. The urinary biomarker levels were normalized using the concentration of creatinine in the samples. The Jaffé reaction was employed to determine the creatinine concentration in the samples. The data found for creatinine varied from 0.31 to 2.83 g Lurine−1, in concordance with levels found in the literature.25
Table 2 Sample population included in the study together with their gender, type of nicotine consumption system used, smoking time, use of an alternative practice to traditional tobacco and creatinine concentration in urine
Sample Gender Age Weight Practice Smoking time (years) Last year averaged cig per day Alternative practice (months) Nicotine liquid refill concentration (mg mL−1) Consumed volume (mL per day) Vaping solution type free base/salts Living with smokers Creatinine (g Lurine−1)
Sample 01 Man 78 80 Smoker 61 20 No 0.68
Sample 02 Woman 64 59 Smoker 40 13 0.32
Sample 03 Woman 59 59 Smoker 40 10 Yes 0.76
Sample 04 Woman 60 55 Smoker 40 10 Yes 1.92
Sample 05 Man 60 78 Smoker 40 20 Yes 1.38
Sample 06 Man 53 73 Vaper 26 30 132 3 20 Free base No 2.48
Sample 07 Woman 47 70 Vaper 18 15 108 12 2 Free base No 1.98
Sample 08 Woman 48 60 Vaper 24 10 84 0 4 No 0.64
Sample 09 Woman 39 72 Vaper 16 30 99 3/ 10 Free base No 0.96
Sample 10 Woman 40 61 Vaper 28 10 84 5 10 Salts Yes 1.23
Sample 11 Man 54 107 Vaper 30 40 108 6 10 Free base Yes 0.98
Sample 12 Woman 39 90 Vaper 18 40 84 20 4 Salts No 1.59
Sample 13 Woman 40 70 Vaper 18 40 89 20 4 Salts No 0.56
Sample 14 Man 56 90 Vaper 30 40 90 3 40 Free base Yes 0.40
Sample 15 Woman 46 74 Vaper 24 30 84 18 1 Free base No 0.85
Sample 16 Woman 41 61 Vaper 28 10 84 5 10 Salts Yes 0.59
Sample 17 Woman 29 52 Non-smoker 1.25
Sample 18 Woman 34 67 Non-smoker Yes 1.63
Sample 19 Woman 74 70 Non-smoker Yes 1.76
Sample 20 Man 20 63 Non-smoker No 0.87
Sample 21 Woman 75 76 Non-smoker Yes 2.09
Sample 22 Woman 29 52 Non-smoker 2.60
Sample 23 Man 44 77 Non-smoker 2.05
Sample 24 Man 21 60 Non-smoker No 1.18
Sample 25 Man 52 110 Vaper 23 6 86 0 2 Free base Yes 1.34
Sample 26 Woman 33 67 Non-smoker Yes 0.68
Sample 27 Woman 34 65 Non-smoker Yes 0.59
Sample 28 Man 44 77 Non-smoker 0.58
Sample 29 Man 68 81 Non-smoker Yes 0.87
Sample 30 Man 69 74 Non-smoker Yes 1.88
Sample 31 Woman 21 50 Non-smoker Yes 0.35
Sample 32 Man 52 110 Vaper 23 6 86 0 2 Free base Yes 0.77
Sample 33 Woman 28 52 Non-smoker No 1.51
Sample 34 Woman 21 50 Non-smoker Yes 0.85
Sample 35 Woman 75 70 Non-smoker Yes 0.48
Sample 36 Woman 76 68 Non-smoker Yes 0.66
Sample 37 Woman 28 52 Non-smoker No 0.63
Sample 38 Woman 16 42 Non-smoker No 0.67


Evaluation of 3HPMA

Analytical features of the 3HPMA. The analytical procedure employed has been validated in terms of linearity, sensitivity accuracy and precision. A 0.9974 determination coefficient value (R2) was obtained for the linear calibration range from 9 ng mL−1 to 750 ng mL−1. The limits of detection (LOD) and quantification (LOQ) were calculated as 3 and 10 times, respectively, the standard deviation of the intercept of the calibration line divided by the calibration slope. Values of 3 and 9 ng mL−1 were obtained for the instrumental LOD and LOQ, respectively, of 3HPMA in urine samples. These data were confirmed with the 3 and 10 ratio signal/noise in the chromatogram. On the other hand, the accuracy of the method was established from the recovery of spiked urine samples (n = 3). Table 3 indicates the recovery values found. It can be seen that the values varied from 93% around the LOQ to 103% at the highest spiked concentration level. The precision of the measurements, evaluated as the relative standard deviation (RSD%), ranged from 1 to 5%.
Table 3 Recovery values obtained for 3HPMA determination in spiked urine samples
C added (ng mL−1 ± s (RSD%, n = 3))
9 50 100 250 500 750
Recovery (%) 93 ± 2 (2) 91 ± 4 (4) 98 ± 5 (5) 97 ± 1 (1) 96 ± 2 (2) 103 ± 4 (4)


Analysis of urine samples. Table 4 indicates the concentration of the acrolein metabolite 3HPMA found in urine samples normalized to their respective creatinine concentrations. It should be highlighted that the highest 3HPMA concentrations were obtained for smokers, with a smoking history equal to or more than forty years. The 3HPMA values found were in concordance with those reported in the literature for smokers' urine.26 On the other hand, low 3HPMA concentrations were found for non-smokers, spanning 207 to 927 μg gcreatinine−1, in good agreement with those found by other authors.27–30 For vapers, the 3HPMA concentration found in urine ranged from 172 to 1064 μg gcreatinine−1, showing a situation between that of smokers and non-smokers and similar to that found by Bjurlin et al.31
Table 4 3HPMA concentrations, expressed as μg gcreatinine−1, in analyzed urine samples
3HPMA concentration in urine (μg gcreatinine−1)
Sample 01 1924.33 Sample 14 737.27 Sample 27 335.82
Sample 02 2543.66 Sample 15 1064.38 Sample 28 356.51
Sample 03 2675.10 Sample 16 757.32 Sample 29 374.31
Sample 04 2860.00 Sample 17 207.43 Sample 30 401.02
Sample 05 3105.97 Sample 18 228.45 Sample 31 482.65
Sample 06 172.12 Sample 19 235.26 Sample 32 529.81
Sample 07 236.12 Sample 20 251.53 Sample 33 533.74
Sample 08 979.97 Sample 21 254.87 Sample 34 620.97
Sample 09 284.26 Sample 22 271.37 Sample 35 643.37
Sample 10 819.04 Sample 23 286.11 Sample 36 709.05
Sample 11 475.71 Sample 24 301.95 Sample 37 768.61
Sample 12 726.54 Sample 25 324.52 Sample 38 927.24
Sample 13 1048.26 Sample 26 325.60


Can be vaping a kind of cessation?. Fig. 1 shows the average of the 3HPMA values for smokers and non-smokers, together with their respective standard deviations. An averaged 880 ± 150 μg gcreatinine−1 3HPMA concentration was found for heavy smokers who had replaced the smoking of tobacco by nicotine vaping systems for 80–100 months, with the 3HPMA concentration in urine found to have fallen to an average 330 ± 130 μg gcreatinine−1 concentration for those who had replaced traditional smoking practices for a duration of 100–120 months. In short, a quadratic relationship can be established between the 3HPMA/creatinine levels and the duration of replacement of traditional smoking by vaping, providing a value for the memory tobacco time of approximately 10 years.
image file: d4ay00444b-f1.tif
Fig. 1 Evolution with time using alternative practices for 3HPMA concentration, expressed as μg gcreatinine−1, found in the urine of former smokers who have substituted smoking by vaping compared with [3HPMA]averaged ± SD found in smokers' (image file: d4ay00444b-u1.tif) and non-smokers' (image file: d4ay00444b-u2.tif) urine.

Conclusions

An evaluation of the 3HPMA/creatinine relationship in the urine samples of smokers who actively burn tobacco, and those who have replaced smoking by nicotine vaping seems to indicate a relationship between the persistence of 3HPMA and the duration of using an alternative practice of nicotine consumption. This relationship provides an approximate value of 10 years, or 120 months, for the tobacco memory effect of the acrolein metabolite.

Ethical statement

The presented project was approved by Ethics Committee of the University of Valencia (Valencia, Spain), verification code X0H21EQATBAG6TVF. Volunteers enrolled in the study have provided their written informed consent for the research study protocol.

Data availability

The data underlying this article will be shared on reasonable request to the corresponding author.

Conflicts of interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgements

The present study has been co-funded by “Contrato de investigación ESPAÑA SALUD-UNIVERSITAT DE VALENCIA para el desarrollo del Proyecto: Evaluación de marcadores en orina de riesgo para la salud de fumadores que hayan reemplazado el Tabaco tradicional por HNB o vapeo” (CPI-21-147) and the European Union through the European Regional Development Fund Operational Programme (ERDF) of the Valencian Region (2014–2020). The European Commission financed the analytical instruments used here through the European Regional Development Funds (ERDF) Operation Program of the Valencian Region (2014–2020).

References

  1. National Center for Chronic Disease Prevention and Health Promotion (US) Office on Smoking and Health, The Health Consequences of Smoking—50 Years of Progress: A Report of the Surgeon General, Centers for Disease Control and Prevention (US), Atlanta (GA), 2014, (Last accessed 2023 January), https://www.ncbi.nlm.nih.gov/books/NBK179276/ Search PubMed.
  2. World Health Organization (WHO), WHO report on the global tobacco epidemic, 2023: protect people from tobacco smoke, (Last accessed 2023 January), https://iris.who.int/bitstream/handle/10665/372043/9789240077164-eng.pdf?sequence=1 Search PubMed.
  3. US Department of Health and Human Services (USDHHS), How Tobacco Smoke Causes Disease: the Biology and Behavioral Basis for Smoking-Attributable Disease: a Report of the Surgeon General. Available via How Tobacco Smoke Causes Disease: the Biology and Behavioral Basis for Smoking-Attributable Disease, Introduction, Chapter 1: Evaluation of Evidence on Mechanisms of Disease Production, and Summary, Centers for Disease Control and Prevention (US), Atlanta (GA), 2010, (Last accessed 2023 January), https://www.ncbi.nlm.nih.gov/books/NBK53017/ Search PubMed.
  4. C. M. Chang, Y. Cheng, T. M. Cho, E. V. Mishina, A. Y. Del Valle-Pinero, D. M. van Bemmel and D. K. Hatsukami, Nicotine Tob. Res., 2019, 21(1), 3–13,  DOI:10.1093/ntr/ntx273.
  5. C. M. Chang, S. H. Edwards, A. Arab, A. Y. Del Valle-Pinero, L. Yang and D. K. Hatsukami, Cancer Epidemiol., Biomarkers Prev., 2017, 26(3), 291–302,  DOI:10.1158/1055-9965.EPI-16-0675.
  6. Center for Tobacco Products/U. S. Food and Drug Administration, Harmful and Potentially Harmful Constituents in Tobacco Products and Tobacco Smoke, Established List, 2012, (Last accessed 2023 January), https://www.fda.gov/downloads/TobaccoProducts/GuidanceComplianceRegulatoryIInfomation/UCM297981.pdf Search PubMed.
  7. US Department of Health and Human Services (USDHHS), Chapter 3: Chemistry and Toxicology of Cigarette Smoke and Biomarkers of Exposure and Harm, How Tobacco Smoke Causes Disease: the Biology and Behavioural Basis for Smoking-Attributable Disease: a Report of the Surgeon General, Centers for Disease Control and Prevention (US), Atlanta (GA), 2010, (Last accessed 2023 January), https://www.ncbi.nlm.nih.gov/books/NBK53014/#ch3.s14 Search PubMed.
  8. Biomarkers of Tobacco Use: Relevance to Tobacco Harm Reduction, in Biomarkers in Toxicology. Biomarkers in Disease: Methods, Discoveries and Applications, ed. E. K. Round, K. Marano, V. B. Patel, V. R. Preedy and R. Rajendram, Springer, Cham, 2023,  DOI:10.1007/978-3-031-07392-2_51.
  9. N. Gale, M. McEwan, O. M. Camacho, G. Hardie, C. J. Proctor and J. Murphy, Emerg. Med., 2021, 16, 2201–2212,  DOI:10.1007/s11739-021-02798-6.
  10. N. Gale, M. McEwan, G. Hardie, J. P. Christopher and J. Murphy, Ann. Emerg. Med., 2022, 17, 2017–2030,  DOI:10.1007/s11739-022-03062-1.
  11. D. Gallart-Mateu, P. Dualde, C. Coscollà, J. M. Soriano, S. Garrigues and M. de la Guardia, Anal. Bioanal. Chem., 2023, 415, 6677–6688,  DOI:10.1007/s00216-023-04943-w.
  12. S. M. Jeong, J. E. Yoo, J. Park, W. Jung, K. N. Lee, K. Han, C. M. Lee, K. W. Nam, S. P. Lee and D. W. Shin, Cardiovasc. Diabetol., 2023, 22(1), 193,  DOI:10.1186/s12933-023-01930-4.
  13. R. Polosa, J. B. Morjaria, P. Caponnetto, U. Prosperini, C. Russo, A. Pennisi and C. M. Bruno, Respir. Res., 2016, 17(1), 166,  DOI:10.1186/s12931-016-0481-x.
  14. S. Huang, O. Tang, X. Zheng, H. Li, Y. Wu and L. Yang, Arch. Pub. Health, 2023, 81, 101,  DOI:10.1186/s13690-023-01111-5.
  15. A. F. Fares, Y. Li, M. Jiang, M. C. Brown, A. C. L. Lam, R. Aggarwal, S. Schmid, N. B. Leighl, F. A. Shepherd, Z. Wang, N. Diao, A. S. Wenzlaff, J. Xie, T. Kohno, N. E. Caporaso, C. Harris, H. Ma, M. J. Barnett, L. F. Leal, G. Fernandez-Tardon, M. Pérez-Ríos, M. P. A. Davies, F. Taylor, B. Schöttker, P. Brennan, D. Zaridze, I. Holcatova, J. Lissowska, B. Świątkowska, D. Mates, M. Savic, H. Brenner, A. Andrew, A. Cox, J. K. Field, A. Ruano-Ravina, S. S. Shete, A. Tardon, Y. Wang, L. L. Marchand, R. M. Reis, M. B. Schabath, C. Chen, H. Shen, B. M. Ryan, M. T. Landi, K. Shiraishi, J. Zhang, A. G. Schwartz, M. S. Tsao, D. C. Christiani, P. Yang, R. J. Hung, W. Xu and G. Liu, Lancet Public Health, 2023, 8(9), e691–e700,  DOI:10.1016/S2468-2667(23)00131-7.
  16. U.S. Department of Health & Human Services. Center for disease Control and Prevention (CDC), Smoking & Tobacco use Benefits of Quitting, 2023, https://www.cdc.gov/tobacco/quit_smoking/how_to_quit/benefits/index.htm, (last accessed 30 April 2024).
  17. R. Philip Yeager, M. Kushman, S. Chemerynski, R. Weil, X. Fu, M. White, P. Callahan-Lyon and H. Rosenfeldt, Toxicol. Sci., 2016, 151(2), 347–364,  DOI:10.1093/toxsci/kfw051.
  18. R. Shi, T. Rickett and W. Sun, Mol. Nutr. Food Res., 2011, 55, 1320–1331,  DOI:10.1002/mnfr.201100217.
  19. Z. Feng, W. Hu, Y. Hu and M. S. Tang, Proc. Natl. Acad. Sci. U. S. A., 2006, 103, 15404–115409,  DOI:10.1073/pnas.0607031103.
  20. P. Hikisz and D. Jacenik, Cells, 2023, 12(6), 879,  DOI:10.3390/cells12060879.
  21. S. G. Carmella, M. Chen, Y. Zhang, S. Zhang, D. K. Hatsukami and S. S. Hecht, Chem. Res. Toxicol., 2007, 20, 986–990,  DOI:10.1021/tx700075y.
  22. T. Schettgen, A. Musiol and T. Kraus, Rapid Commun. Mass Spectrom., 2008, 22, 2629–2638,  DOI:10.1002/rcm.3659.
  23. W. Yan, G. D. Byrd, B. G. Brown and M. F. Borgerding, J. Chromatogr. Sci., 2010, 48, 194–199,  DOI:10.1093/chromsci/48.3.194.
  24. J. Park, N. H. Kwon, S. Y. Kim, B. J. Ko and J. Y. Kim, J. Anal. Sci. Technol., 2023, 14(1), 41,  DOI:10.1186/s40543-023-00397-y.
  25. L. Perbellini, N. Veronese and A. Princivalle, J. Chromatogr. B: Anal. Technol. Biomed. Life Sci., 2002, 781, 269–290,  DOI:10.1016/S1570-0232(02)00501-9.
  26. K. Higashi, K. Igarashi and T. Toida, Biol. Pharm. Bull., 2016, 39(6), 915–919,  DOI:10.1248/bpb.b15-01022.
  27. A. S. Cravo, J. Bush, G. Sharma, R. Savioz, C. Martin, S. Craige and T. Walele, Regul. Toxicol. Pharmacol., 2016, 81(1), S1–S14,  DOI:10.1016/j.yrtph.2016.10.003.
  28. C. Sakaguchi, A. Kakehi, N. Minami, A. Kikuchi and Y. Futamura, Regul. Toxicol. Pharmacol., 2014, 69(3), 338–347,  DOI:10.1016/j.yrtph.2014.04.016.
  29. A. Morin, C. J. Shepperd, A. C. Eldridge, N. Poirier and R. Voisine, Regul. Toxicol. Pharmacol., 2011, 61(3), S3–S12,  DOI:10.1016/j.yrtph.2010.09.020.
  30. C. J. Shepperd, A. C. Eldridge, D. C. Mariner, M. McEwan, G. Errington and M. Dixon, Regul. Toxicol. Pharmacol., 2009, 55(1), 97–109,  DOI:10.1016/j.yrtph.2009.06.006.
  31. M. A. Bjurlin, R. S. Matulewicz, T. R. Roberts, B. A. Dearing, D. Schatz, S. Sherman, T. Gordon and O. El Shahawy, Eur. Urol. Oncol., 2021, 4(5), 766–783,  DOI:10.1016/j.euo.2020.02.004.

This journal is © The Royal Society of Chemistry 2024
Click here to see how this site uses Cookies. View our privacy policy here.