Graphical abstract
Keywords: Cigarettes mainstream smoke, Reference cigarettes, Cigarettes in vitro toxicity
Highlights
-
•
3R4F Kentucky reference cigarettes stock is depleting.
-
•
3R4F reference cigarettes have been widely used as monitor or comparator.
-
•
1R6F reference cigarettes are a suitable replacement for 3R4F on the basis of smoke chemistry and in vitro assays.
Abstract
A new Kentucky reference cigarette, 1R6F, has been manufactured to replace the depleting 3R4F reference cigarette. The 3R4F Kentucky reference cigarettes have been widely used as monitor or comparator cigarettes for mainstream smoke analysis and in vitro and in vivo toxicological data of cigarettes and novel tobacco products. Both reference cigarettes were analyzed in the same laboratory during the same period of time with the goal of performing a comparison of 3R4F and 1R6F. On the basis of the results obtained from aerosol chemistry and in vitro assays, we consider that the 1R6F reference cigarette is a suitable replacement for the 3R4F reference cigarette as a comparator/monitor cigarette. Its specific use as a comparator for novel tobacco products was checked on the basis of a comparative test with the Tobacco Heating System 2.2 as an example.
1. Introduction
The availability of reference cigarettes, prepared with a minimum of cigarette to cigarette variability and in quantities sufficient to cover a long period of time, is critical for laboratories performing smoke chemistry, in vitro testing, or in vivo analyses for cigarettes, novel tobacco products, and e-cigarettes, because reference cigarettes allow for the replication and the comparison over time of the test results obtained in other laboratories. In addition, reference cigarettes provide the most direct link between results obtained in each of the different pre-clinical trials mentioned above. Historically, the University of Kentucky provided such reference cigarettes, differing in their design and specifications, with the aim to represent various segments of the U.S. cigarette market. Lately, the Kentucky reference cigarette 3R4F has been widely used as a monitor or a comparator cigarette for mainstream smoke (MS) analyses and in vitro and in vivo toxicological assays. It has been regularly used as a monitor in collaborative tests organized for the analysis of MS constituents [[1], [2], [3]], or in the frame of methods development [[4], [5], [6], [7], [8], [9]], as a comparator for analyses performed for cigarettes [4,[10], [11], [12], [13], [14], [15]] or heated tobacco products [[16], [17], [18], [19], [20], [21], [22], [23]]. It has also been used as a comparator for toxicological in vitro assays for cigarettes [[24], [25], [26], [27]] or novel tobacco products and e-cigarettes [20,26,[28], [29], [30], [31], [32], [33], [34], [35], [36], [37], [38]] and in vivo toxicological studies [[39], [40], [41], [42], [43], [44], [45], [46]]. The stock for 3R4F reference cigarette is, however, depleting. Therefore, and upon service agreement with the U.S. Food and Drug Administration, the University of Kentucky produced 50 million cigarettes of a new Kentucky reference cigarette, 1R6F, in 2015, according to the specifications provided by the University of Kentucky (e.g., cigarette dimensions, amount of tobacco per cigarette, resistance to draw) [47]. Table 1 provides a comparison of the main cigarette design parameters of both 3R4F and 1R6F reference cigarettes.
Table 1.
Parameter | 3R4F (2006) | 1R6F (2015) |
---|---|---|
Blend (%) | ||
Flue Cured | 35.4 | 34 |
Burley | 21.6 | 24 |
Maryland | 1.4 | – |
Oriental | 12.1 | 12 |
Reconstituted | 29.6 | 20 |
Expanded Flue Cured | 7 | |
Expanded Burley | – | 3 |
Cigarette Design | ||
Cigarette Length | 84 mm | 83 mm |
Tobacco Rod Circumference | 24.8 mm | 24.6 mm |
Tobacco Rod Length | 57 mm | 56 mm |
Resistance to Draw | 128 mm H2O | 107 |
Humectants (%) | ||
Glycerol | 2.7 | 1.7 |
Propylene glycol | – | 1% |
Isosweet | 6.4 | 6.3% |
Cigarette Paper | ||
Banded (CORESTA units) | – | 9 |
Base (CORESTA units) | 24 | 46 |
Filter Ventilation (%) | 29 | 33 |
Yield data from supplier | ||
Puff count | 9.0 | 7.5 |
TPM (mg/cig) | 11.0 | 10.0 |
‘Tar’ (mg/cig) | 9.4 | 8.6 |
Nicotine (mg/cig) | 0.7 | 0.7 |
Carbon monoxide (mg/cig) | 12.0 | 10.1 |
The 1R6F Kentucky reference cigarette has been used as a monitor or a comparator cigarette until now only in a limited number of cases, such as a comparator to heated tobacco products and e-cigarettes in in vitro or aerosol composition studies [19,48,49], in a smoking topography study [50], or for small cigar and cigarette studies [51,52]. It has also been used as a reference in a recently published recommended method of CORESTA [53].
The goal of the present study is to compare the MS chemistry and the in vitro cytotoxicity mutagenicity, and genotoxicity using standard assays, of the two Kentucky reference cigarettes, 3R4F and 1R6F. Such a comparison is necessary to determine whether both reference cigarettes are interchangeable or sufficiently similar to consider previous conclusions from a range of scientific studies performed with the 3R4F reference cigarette to be equally valid considering the chemistry and toxicity of the 1R6F reference cigarette. Such a study was performed in the past for the 2R4F (predecessor of 3R4F) and 3R4F reference cigarettes, and it was suggested that they were equivalent in terms of smoke chemistry and in vitro and in vivo toxicity [39].
2. Methods
2.1. MS analyses
The analyses were performed under Good Laboratory Practices at Labstat International ULC. The cigarette MS was generated under ISO [54] and ISO Intense [55] analytical smoking machine conditions. The cigarettes were conditioned before analysis according to standardized conditions [56].
The list of compounds analyzed in the MS and the related methods correspond to what was applied to the 3R4F cigarette in an already published article [20]. Four replicates per analysis were performed. The list covers common lists of harmful and potentially harmful constituents (HPHC), such as the World Health Organization-39 list [57] or the Health Canada list required for the reporting of commercial brands in Canada [58].
2.2. In vitro assay analyses
The mainstream cigarette smoke total particulate matter (TPM) was generated under ISO [54] and ISO Intense [55] analytical smoking machine conditions and extracted to a stock concentration of 10 mg/mL in dimethylsulfoxide. In addition, the mainstream gas vapor phase (GVP) was generated and tested in the neutral red uptake (NRU) assay only. The Health Canada methods T501, T502, and T503 [58] were applied to the Ames assay, NRU assay, and in vitro micronucleus (ivMN) assay, respectively. The vehicle and positive controls in each assay and on each day of testing were within the historical control ranges used in this laboratory; therefore, the assays were considered valid.
2.3. Statistical treatment of data
The overall rationale for the comparative assessment between the 1R6F and 3R4F Kentucky reference cigarettes is based on the fundamental notion of long-term analytical variability. In the context of a single batch of reference monitor test pieces manufactured at a single point in time, the long-term analytical variability [12] represents the natural variation from analytical results obtained in different studies conducted within the same laboratory, using the same methods but at different points in time. For each constituent and specified analytical smoking machine condition, the long-term analytical variability was empirically estimated through one year of measurements conducted on the 3R4F reference cigarette at Labstat International ULC. The magnitude of the difference between 3R4F and 1R6F is evaluated constituent by constituent against the corresponding inherent precision of the analytical method over time, which is essentially driven by the long-term variability for each constituent.
For each of the constituents above the limit of quantification (LOQ) in the 3R4F monitor test piece reference data set, the critical differences for differences of means of two single point in time measurements between 3R4F and 1R6F are defined to be [59]:
where RSD[%] stands for the relative standard deviation in percent of the 3R4F monitor data set for the given constituent, and n = number of replicates (i.e., four replicates, as per the sample testing scheme). The performance of the 3R4F and 1R6F reference cigarettes are deemed comparable if the absolute percentage differences per constituent are within the performance boundaries expressed by the critical differences.
For endpoints where some replicates are below LOQ in the 3R4F monitor reference data set, the average yields are compared to a threshold established as 4*LOQ.
3. Results
3.1. MS chemistry
The relative percent differences for the mean individual HPHC deliveries of 1R6F cigarettes to 3R4F cigarettes were compared to the long-term 3R4F deliveries variability, according to a previously described method [12,60].
A graphical representation of the differences observed between 1R6F and 3R4F cigarettes is provided in Fig. 1.
Compounds not included in the critical difference statistical analysis, due to non-quantifiable results, include arsenic, chromium, lead, nickel, selenium, nitrobenzene, and resorcinol.
Statistically significant increases were observed for ammonia, formaldehyde, phenol, quinoline, acetamide, acrylamide, and propylene oxide under the ISO smoking regime and for propylene oxide using the ISO Intense smoking regime for 1R6F cigarettes.
Statistically significant decreases were observed for NO, NOx, NNK, NNN, and vinyl chloride under the ISO smoking regime and for 4-aminobiphenyl, acetaldehyde, acetone, butyraldehyde, MEK, propionaldehyde, NO, NOx, CO, NAB, NAT, NNK, and NNN under the ISO Intense smoking regime for 1R6F cigarettes (Fig. 2).
3.2. In vitro analyses
The 3R4F results for all in vitro assays and treatment conditions were within the expected (historical) range of 3R4F assay responses when the TPM was generated under intense smoking conditions. No historical ranges for the in vitro assays were calculated for the 3R4F MS when generated under ISO smoking conditions due to a lack of sufficient data.
3.2.1. In vitro bacterial mutagenicity
Following treatment with the 3R4F and 1R6F TPM, concentration-related and reproducible increases in revertants were observed in tester strains TA98, TA100, and TA1537 in the presence of S9 and in TA98 in the absence of S9 compared to solvent control when the cigarettes were smoked under ISO and ISO Intense smoking conditions. In the remaining strains and treatment conditions, no reproducible increase in revertants reproducible was observed. For these tester strains that have been proven to be responsive to TPM, the specific mutagenicity (Ames assay-specific activity slope) was determined. Then, the relative % difference in specific mutagenicity between the 1R6F and the 3R4F was compared to the 3R4F long-term variability.
This assessment showed that for the Ames assay, in any of the used strains in the presence and absence of S9 metabolic activation, the relative differences observed between the 1R6F- and 3R4F-specific mutagenicity did not exceed the calculated 3R4F long-term variability for the ISO or ISO Intense smoking regime, as shown in Table 3 and illustrated in Fig. 3.
Table 3.
Note: statistical analysis not done because at least one test item was determined to be non-mutagenic overall.
The relative (%) difference is compared to the calculated 3R4F long-term variability for the assay statistic to determine if the difference exceeds the long-term variability of the Ames test method.
3.2.2. In vitro cytotoxicity (NRU assay)
In the NRU assay, the TPM and GVP samples generated under ISO and ISO Intense smoking conditions induced concentration-related decreases in cell viability, and an IC50 value could be derived in each instance. The relative differences observed between the 1R6F and 3R4F response statistics for the NRU assay analysis did not exceed the calculated 3R4F reference item variability in any of the relevant smoking regimes or smoke fractions, as shown in Table 4 and illustrated in Fig. 4.
Table 4.
1R6F IC50 | 3R4F IC50 | Mean IC50 Comparisons | ||||||||
---|---|---|---|---|---|---|---|---|---|---|
[mg/mL] |
[mg/mL] |
|||||||||
Smoking Regime3 | Assay | Smoke Fraction4 | Cigarette Comparison | 3R4F Reference Item Cigarette Variability (%) | Average | Std. Dev. | Average | Std. Dev. | Observed Relative Diff. (%) | Observed Exceeds 3R4F Variability? |
ISO | NRU | TPM | 1R6F vs. 3R4F | 37.1 | 68.4 | 10.4 | 69.9 | 13.2 | −2.2 | no |
ISO | NRU | GVP | 1R6F vs. 3R4F | 33.3 | 160.5 | 39.6 | 136.0 | 17.2 | 18.0 | no |
Intense | NRU | TPM | 1R6F vs. 3R4F | 37.1 | 72.2 | 12.6 | 68.6 | 1.4 | 5.2 | no |
Intense | NRU | GVP | 1R6F vs. 3R4F | 33.3 | 149.5 | 10.0 | 130.2 | 14.6 | 14.9 | no |
Note: The relative (%) difference is compared to the calculated 3R4F long-term variability for the assay statistic to determine if the difference exceeds the long-term variability of the NRU test method.
3.2.3. In vitro genotoxicity (ivMN assay)
When the 1R6F and 3R4F TPMs were tested in the ivMN assay, the assay response exhibited an overall genotoxic response in each treatment condition (schedule (i), (ii), (iii)) and for each smoking regime. The schedules (i), (ii) and (iii) correspond to the schedules described in the Health Canada method T-503 [58] and correspond respectively to a short-term exposure of the cells in the absence of metabolic activation, a short-term exposure of the cells in the presence of metabolic activation and to a long-term exposure of the cells in the absence of metabolic activation. The relative difference observed between the 1R6F and 3R4F response statistics for the ivMN assay analysis did not exceed the calculated 3R4F long-term variability, with the exception of schedule (i) (short-term exposure in the absence of S9) when the TPM was generated under the ISO smoking regime, as shown in Table 5 and illustrated in Fig. 5.
Table 5.
Linear Regression Slope Comparisons | |||||||
---|---|---|---|---|---|---|---|
Smoking Regime2 | Schedule | Brand Comparison | 3R4F Reference Item Cigarette Variability | 1R6F Linear Regression Slope | 3R4F Linear Regression Slope | Observed Relative Diff. | Observed Exceeds 3R4F Variability? |
(%) | (No. of MN/ (mg TPM/mL)) | (No. of MN/ (mg TPM/mL)) | (%) | ||||
ISO | Schedule (i) | 1R6F vs. 3R4F | 15.3 | 61.5 | 51.9 | 18.5 | yes |
ISO | Schedule (ii) | 1R6F vs. 3R4F | 22.6 | 30.1 | 29.9 | 0.9 | no |
ISO | Schedule (iii) | 1R6F vs. 3R4F | 17.7 | 63.9 | 60.9 | 5.0 | no |
Intense | Schedule (i) | 1R6F vs. 3R4F | 15.3 | 57.6 | 51.4 | 12.2 | no |
Intense | Schedule (ii) | 1R6F vs. 3R4F | 22.6 | 34.7 | 33.0 | 5.0 | no |
Intense | Schedule (iii) | 1R6F vs. 3R4F | 17.7 | 56.8 | 63.5 | −10.6 | no |
Note: The relative (%) difference is compared to the calculated 3R4F long-term variability for the assay statistic to determine if the difference exceeds the long-term variability of the ivMN test method.
3.3. Use of 3R4F or 1R6F as a comparator for heated tobacco products
The 3R4F cigarette has been used as a comparator for the aerosol composition of heated tobacco products [[17], [18], [19], [20],22,26], using different lists of HPHCs, with an average reduction of about 90% (e.g., for the Tobacco Heating System (THS) 2.2) across a broad range of chemical compounds in comparison with 3R4F [16]. It was also confirmed that the average reduction in aerosol yields for THS 2.2 when compared with 3R4F was equally valid for commercial cigarettes sampled worldwide [16].
The use of 1R6F and 3R4F cigarettes as comparators for the aerosol composition of a specific heated tobacco product, THS 2.2, is provided in the Fig. 6 below.
Using the results provided in Table 1 for 3R4F and 1R6F cigarettes and the results previously published for THS 2.2 [16], there is an average reduction of 93% and 92% across the Health Canada list of HPHCs for 3R4F and 1R6F cigarettes, respectively, or 91% across the full list provided in Table 2 in comparison with both 3R4F and 1R6F cigarettes.
Table 2.
HPHC | 3R4F ISO Mean | 3R4F ISO SD | 3R4F intense Mean | 3R4F intense SD | 1R6F ISO Mean | 1R6F ISO SD | 1R6F intense Mean | 1R6F intense SD |
---|---|---|---|---|---|---|---|---|
Nicotine [mg/cig] | 0,702 | 0,042 | 1,99 | 0,13 | 0,778 | 0,052 | 1,90 | 0,05 |
2,02 | 2,00 | 0,08 | ||||||
CO [mg/cig] | 10,0 | 0,6 | 30,5 | 1,8 | 10,2 | 0,4 | 26,2 | 0,6 |
32,0 | 1,0 | 29,4 | 0,6 | |||||
Ammonia [μg/cig] | 9,64 | 1,06 | 34,0 | 0,5 | 12,5 | 0,5 | 35,9 | 1,7 |
32,5 | 3,5 | 34,7 | 2,0 | |||||
Formaldehyde [μg/cig] | 24,7 | 2,4 | 87,1 | 7,4 | 33,5 | 3,7 | 104 | 9 |
54,1 | 6,0 | 68,4 | 3,9 | |||||
Acetaldehyde [μg/cig] | 597 | 13 | 1838 | 105 | 532 | 9 | 1601 | 137 |
2200 | 103 | 1859 | 169 | |||||
Acetone [μg/cig] | 241 | 7 | 749 | 44 | 209 | 7 | 635 | 57 |
660 | 24 | 520 | 42 | |||||
Acrolein [μg/cig] | 53,2 | 1,4 | 180 | 13 | 51,8 | 2,1 | 173 | 17 |
159 | 9 | 148 | 22 | |||||
Propionaldehyde [μg/cig] | 43,0 | 1,1 | 135 | 8 | 39,1 | 0,9 | 119 | 11 |
132 | 3 | 116 | 13 | |||||
Crotonaldehyde [μg/cig] | 9,89 | 0,63 | 59,5 | 4,4 | 10,0 | 0,6 | 55,0 | 5,9 |
42,0 | 6,2 | 39,5 | 3,2 | |||||
Methyl Ethyl Ketone [μg/cig] | 57,7 | 2,4 | 199 | 13 | 49,2 | 2,6 | 164 | 16 |
192 | 8 | 150 | 14 | |||||
Butyraldehyde [μg/cig] | 28,4 | 0,7 | 93,0 | 4,3 | 25,9 | 1,0 | 80,3 | 7,7 |
60,9 | 5,1 | 51,5 | 7,3 | |||||
HCN [μg/cig] | 91,5 | 8,3 | 390 | 23 | 98,3 | 14,0 | 352 | 10 |
343 | 62 | 332 | 43 | |||||
Mercury [ng/cig] | 2,10 | 0,03 | 4,92 | 0,06 | 1,97 | 0,13 | 4,68 | 0,24 |
4,26 | 0.50 | 3,89 | 0,32 | |||||
Cadmium [ng/cig] | 24,5 | 2,0 | 93,2 | 7,4 | 26,1 | 2,3 | 76,1 | 1,2 |
105 | 5 | 88,8 | 1,9 | |||||
Lead [ng/cig] | <LOQ | NA | <LOQ | NA | <LOQ | NA | <LOQ | NA |
28,7 | 0,8 | 28,1 | 0,6 | |||||
Chromium [ng/cig] | <LOD | NA | <LOD | NA | <LOD | NA | <LOD | NA |
<LOQ | NA | <LOQ | NA | |||||
Nickel [ng/cig] | <LOD | NA | <LOD | NA | <LOD | NA | <LOD | NA |
<LOQ | NA | <LOQ | NA | |||||
Arsenic [ng/cig] | <LOQ | NA | <LOQ | NA | <LOQ | NA | <LOQ | NA |
8,01 | 0.56 | 7,57 | 0,27 | |||||
Selenium [ng/cig] | <LOD | NA | <LOD | NA | <LOD | NA | <LOD | NA |
<LOQ | NA | <LOQ | NA | |||||
NO [μg/cig] | 196 | 9 | 471 | 17 | 132 | 6 | 329 | 13 |
495 | 16 | 357 | 24 | |||||
NOx [μg/cig] | 211 | 9 | 524 | 17 | 143 | 6 | 369 | 15 |
405 | 26 | |||||||
555 | 19 | |||||||
Pyridine [μg/cig] | 7,46 | 1,34 | 35,2 | 6,4 | 6,83 | 0,73 | 36,4 | 4,6 |
28,6 | 2,8 | 30,4 | 2,4 | |||||
Quinoline [μg/cig] | 0,136 | 0,009 | 0,315 | 0,033 | 0,207 | 0,015 | 0,331 | 0,041 |
0,389 | 0,028 | 0,427 | 0,009 | |||||
Styrene [μg/cig] | 6,54 | 1,17 | 21,7 | 2,4 | 4,97 | 0,67 | 20,4 | 2,3 |
14,8 | 0,9 | |||||||
16,1 | 2,0 | |||||||
Nitrobenzene [μg/cig] | <LOD | NA | <LOD | NA | <LOD | NA | <LOD | NA |
<LOD | NA | <LOD | NA | |||||
Hydroquinone [μg/cig] | 32,4 | 1,0 | 78,1 | 6,5 | 36,7 | 1,8 | 84,2 | 5,6 |
88,7 | 6,2 | |||||||
84,2 | 1,8 | |||||||
Resorcinol [μg/cig] | <LOD | NA | <LOQ | NA | <LOQ | NA | <LOQ | NA |
1,80 | 0,15 | |||||||
1,57 | 0,22 | |||||||
Catechol [μg/cig] | 39,5 | 1,5 | 86,9 | 5,4 | 43,8 | 1,7 | 91,9 | 5,7 |
87,4 | 3,4 | 91,8 | 5,3 | |||||
Phenol [μg/cig] | 6,99 | 0,36 | 11,1 | 0,9 | 9,13 | 0,58 | 11,7 | 0,6 |
13,5 | 0,8 | 12,5 | 0,6 | |||||
p-Cresol [μg/cig] | 4,47 | 0,22 | 6,83 | 0,53 | 5,16 | 0,21 | 6,84 | 0,53 |
8,72 | 0,38 | |||||||
7,77 | 0,41 | |||||||
m-Cresol [μg/cig] | 1,89 | 0,13 | 2,77 | 0,19 | 2,18 | 0,16 | 2,62 | 0,14 |
3,48 | 0,18 | 2,98 | 0,07 | |||||
o-Cresol [μg/cig] | 2,22 | 0,25 | 3,22 | 0,27 | 2,47 | 0,08 | 2,76 | 0,22 |
3,94 | 0,16 | 3,12 | 0,13 | |||||
Pyrene | 37,3 | 0,7 | 91,9 | 7,5 | 40,2 | 0,7 | 88,0 | 6,0 |
79,4 | 7,5 | 68,4 | 10,3 | |||||
Benzo(a) anthracene [ng/cig] | 12,1 | 0,2 | 28,9 | 2,0 | 13,2 | 0,1 | 27,0 | 1,3 |
24,2 | 2,4 | 21,4 | 3,2 | |||||
Benzo(a)pyrene [ng/cig] | 6,30 | 0,21 | 15,1 | 0,6 | 6,94 | 0,17 | 13,8 | 0,3 |
12,9 | 1,3 | 11,4 | 1,7 | |||||
Dibenz(a,h) anthracene [ng/cig] | <LOQ | NA | 1,34 | 0,09 | <LOQ | NA | 1,19 | 0,20 |
0,915 | 0,124 | 0,892 | 0,086 | |||||
1,3-Butadiene [μg/cig] | 37,9 | 3,1 | 100 | 7 | 39,3 | 3,0 | 102 | 5 |
114 | 4 | |||||||
108 | 4 | |||||||
Isoprene [μg/cig] | 288 | 18 | 799 | 61 | 286 | 24 | 752 | 36 |
887 | 49 | 859 | 46 | |||||
Acrylonitrile [μg/cig] | 5,23 | 0,51 | 20,5 | 1,8 | 5,23 | 0,67 | 19,2 | 1,3 |
18,5 | 1,9 | |||||||
19,5 | 1,6 | |||||||
Benzene [μg/cig] | 33,6 | 2,6 | 88,8 | 6,3 | 33,7 | 2,8 | 82,3 | 4,6 |
78,6 | 4,6 | 76,0 | 5,8 | |||||
Toluene [μg/cig] | 51,4 | 4,8 | 153 | 12 | 47,2 | 4,0 | 132 | 9 |
131 | 5 | 116 | 9 | |||||
Vinyl Chloride [ng/cig] | 39,6 | 3,5 | 94,6 | 7,4 | 31,9 | 2,2 | 84,0 | 3,5 |
109 | 19 | |||||||
95,6 | 9,2 | |||||||
Ethylene oxide [μg/cig] | 6,78 | 0,32 | 19,2 | 1,8 | 5,92 | 0,63 | 17,3 | 0,8 |
19,3 | 2,0 | 17,2 | 0,9 | |||||
Propylene oxide [μg/cig] | 297 | 54 | 1000 | 79 | 657 | 82 | 1710 | 138 |
903 | 308 | 1692 | 232 | |||||
1-Aminonaphthalene [ng/cig] | 14,2 | 1,0 | 29,1 | 2,6 | 13,8 | 1,4 | 26,7 | 0,8 |
17,6 | 0,6 | 17,2 | 0,6 | |||||
2-Aminonapthalene [ng/cig] | 8,77 | 1,11 | 18,1 | 2,3 | 10,7 | 0,8 | 16,2 | 1,3 |
13,2 | 0,8 | 11,8 | 0,9 | |||||
3-Aminobiphenyl [ng/cig] | 2,27 | 0,09 | 5,44 | 0,23 | 2,33 | 0,28 | 4,49 | 0,39 |
3,49 | 0,27 | 3,07 | 0,25 | |||||
4-Aminobiphenyl [ng/cig] | 1,54 | 0,12 | 3,91 | 0,29 | 1,48 | 0,05 | 3,13 | 0,04 |
1,91 | 0,23 | |||||||
2,29 | 0,12 | |||||||
o-Toluidine [ng/cig] | 55,9 | 6,9 | 121 | 1,0 | 59,4 | 4,9 | 109 | 1 |
84,6 | 2,2 | |||||||
83,3 | 2,1 | |||||||
NNN [ng/cig] | 131 | 8 | 337 | 28 | 100 | 9 | 230 | 17 |
263 | 12 | 191 | 8 | |||||
NAT [ng/cig] | 136 | 4 | 334 | 12 | 110 | 10 | 259 | 30 |
246 | 12 | |||||||
268 | 20 | |||||||
NAB [ng/cig] | 13,3 | 0,6 | 31,8 | 1,0 | 11,0 | 1,1 | 24,4 | 2,2 |
24,1 | 1,1 | 21,3 | 1,6 | |||||
NNK [ng/cig] | 113 | 8 | 295 | 32 | 84,5 | 6,0 | 192 | 8 |
281 | 16 | 208 | 7 | |||||
Acetamide [μg/cig] | 2,70 | 0,18 | 12,2 | 1,9 | 3,99 | 0,42 | 13,2 | 1,0 |
11,9 | 1,0 | 14,0 | 1,0 | |||||
Acrylamide [μg/cig] | 1,07 | 0,05 | 3,92 | 0,52 | 1,58 | 0,14 | 3,91 | 0,33 |
3,99 | 0,39 | 4,49 | 0,34 |
Data in italics correspond to the results published by Forster et al [19]. NAB stands for N’-nitrosoanabasine, NAT for N’-nitrosoanatabine, NNN for N’-nitrosonornicotine and NNK for 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone.
4. Discussion
Due to the depletion of 3R4F cigarette stock, there will soon be a need to use other reference cigarettes for comparative or monitoring purposes (e.g., for studies performed for cigarettes and novel tobacco products). The recently produced 1R6F Kentucky reference cigarettes are an obvious candidate to replace the 3R4F Kentucky reference cigarettes. We performed a study that included smoke chemistry and in vitro toxicological assays and used both ISO and ISO Intense smoking regimes, analogous to what was performed in the past to compare the 2R4F (predecessor of 3R4F) and 3R4F reference cigarettes [39].
The MS chemistry of both reference cigarettes, according to the Health Canada list of HPHCs or the wider PMI list [20] obtained under ISO and ISO Intense analytical smoking regimes, has been measured. There are some HPHCs that are either significantly higher or significantly lower in the MS of 1R6F cigarettes when compared with 3R4F cigarettes. It should be noted that with the statistical approach taken in our work [12], one expects to have 0.05*N (where N is the number of HPHC = 58), or about three occurrences of a single HPHC being significantly different when comparing 1R6F and 3R4F. Additionally, it is not expected to have the exact same profile of HPHCs in both reference cigarettes, because the cigarette design is not exactly the same, both in terms of blend (with tobaccos grown in different conditions in terms of soils, locations and environment) and cigarette construction, according to the specifications provided by the University of Kentucky (e.g., cigarette dimensions, filter properties, etc.).
Some HPHCs, such as NO, NOx, NNN, and NNK, are significantly lower in the 1R6F cigarettes than in 3R4F cigarettes with both analytical smoking regimes. Those compounds may all be affected by the blend composition [61]; NO content in smoke is primarily determined by the nitrate content in the tobacco blend [61], and NNN and NNK are typically higher in air-cured tobaccos than in flue-cured tobaccos [62], with a tendency for a downward trend in recent years due to the introduction of new agricultural and curing practices [63,64]. The lower NNN content observed in the MS of 1R6F cigarettes is also observed in the tobacco blend, with reported values for NNN in 1R6F of 2,131 ng/g [47] or 2,294 ng/g [65] and in 3R4F of 2,636 ng/g [66]. However, this is not the case for NNK, for which the reported values are very similar, with values in 1R6F of 676 ng/g [47] and 675 ng/g [65] and in 3R4F of 679 ng/g [66]. The lower value observed for 1R6F MS NNK yields may be due to a lower transfer from tobacco to smoke of NNK, related to a lower amount of bound NNK in the blend [67,68].
Some HPHCs are significantly lower in 1R6F only for one of the two smoking regimes, such as NAB, NAT, vinyl chloride, some aldehyde compounds, CO, or 4-aminobiphenyl. This difference can be due either to the statistical approach mentioned above or to changes in the blend design (e.g., for NAB, NAT, or 4-aminobiphenyl) and/or cigarette design.
One compound, propylene oxide, is significantly higher in 1R6F for both analytical smoking regimes. A possible source for propylene oxide is propylene glycol used as humectant in tobacco blends [69,70]. There is a difference of 1% propylene glycol in the recipes of 1R6F and 3R4F cigarettes (1% in 1R6F; 0% in 3R4F). Gaworski et al. [70] observed an increase of propylene oxide with increasing amounts of added propylene glycol. On the basis of their results, an increase of about 850 ng/cigarette of propylene oxide using the ISO smoking regime could be expected for an addition of 1% propylene glycol, for cigarettes differing only in their amount of added propylene glycol. We observe an increase of 360 ng/cigarette between the 1R6F and the 3R4F using ISO smoking regime, consistent with Gaworski et al. observation, noting that the design of 3R4F and 1R6F cigarettes is not the same.
Finally, some compounds are higher in 1R6F only for one of the two smoking regimes. The remarks provided above for the compounds that are higher in 3R4F cigarette MS are valid in this case, as well.
In terms of in vitro assay results, 1R6F and 3R4F cigarettes displayed similar in vitro cytotoxicity, mutagenicity, and genotoxicity under both smoking conditions, with the exception of a statistically significantly higher response of the 1R6F in the ivMN assay (schedule (i)) under ISO smoking conditions. Considering the smoke chemistry results for the 1R6F and the 3R4F, the increase in ivMN (schedule (i)) may be explained by the increase in acetamide and acrylamide in MS from the 1R6F. Although propylene oxide and formaldehyde were also increased in 1R6F MS, both constituents are mainly in the GVP, and their increase cannot explain the increase in genotoxicity of the 1R6F TPM extract. Most of the carcinogens in TPM (e.g., NNK, NNN, cadmium) were lower in 1R6F TPM or were not different between the cigarettes. Acetamide, which is classified as 2B by the International Agency for Research on Cancer (IARC) [71], is a TPM constituent and was increased by 48% under ISO smoking conditions. Acrylamide, which is classified as 2A by IARC, is also a TPM constituent and was also increased by 48% under ISO smoking conditions.
In the literature, acrylamide did not increase the mutation frequency in bacteria (e.g., TA98 and TA100). Furthermore, there is consistent evidence that activity of acrylamide in cultured mammalian cells was also seen in the absence of an exogenous metabolic activation system, implying that metabolic activation to its metabolite glycidamide might not be necessary to present its genotoxic properties [72]. All in vivo MN assays in mouse bone marrow cells, for example, also showed positive results without exogenous metabolic activation [72].
The toxicological profile of acetamide is less clear. In the literature, acetamide was not mutagenic in the Ames assay [71]. It was marginally positive in the induction of bone marrow micronuclei in male C57BL/6 mice in one study, but it was negative in another study at higher doses in the same species as well as in CBA male mice [71].
In summary, the physicochemical and toxicological profiles of acetamide and acrylamide are capable of explaining the increase in ivMN seen for 1R6F TPM; hence, the two smoke constituents may contribute to this genotoxic effect. However, the question arises why the results of schedule (iii) did not support the results of schedule (i). Furthermore, the 3R4F long-term variability of 15% for the ivMN (schedule (i)) seems to be very low compared with the long-term variabilities seen for the Ames assay and the NRU assay. Therefore, the increase in genotoxicity for 1R6F TPM compared with 3R4F TPM may be a chance finding. Future genotoxicity studies with 1R6F MS will show if the increase in ivMN (schedule (i)) compared with 3R4F MS is reproducible and meaningful.
When 3R4F and 1R6F cigarettes were used as comparison cigarettes to evaluate the aerosol composition of a heated tobacco product, THS 2.2, the average reduction was almost identical with both reference cigarettes. This was also true when comparing the aerosol composition of THS 2.2 with a range of commercially available cigarettes or with 3R4F reference cigarettes [16].
In conclusion, there are some slight differences in terms of smoke chemistry and in vitro assays for the MS of 1R6F and 3R4F reference cigarettes, obtained under ISO and ISO Intense analytical smoking machine regimes. Those differences did not, however, translate into different conclusions regarding the reduction of HPHCs in a heated tobacco product, THS 2.2.
Transparency document
References
- 1.Intorp M., Purkis S. Determination of selected volatiles in cigarette mainstream smoke. The CORESTA 2008 joint experiment. Beitrage zur Tabakforschung International/ Contrib. Tob. Res. 2010;24(4):174–186. [Google Scholar]
- 2.Intorp M., Purkis S., Wagstaff W. Determination of tobacco specific nitrosamines in cigarette mainstream smoke: The CORESTA 2011 collaborative study. Beitrage zur Tabakforschung International/ Contrib. Tob. Res. 2012;25(4):507–519. [Google Scholar]
- 3.Purkis S., Intorp M. Analysis of reference cigarette smoke yield data from 21 laboratories for 28 selected analytes as a guide to selection of new coresta recommended methods. Beitrage zur Tabakforschung International/ Contrib. Tob. Res. 2014;26(2):57–73. [Google Scholar]
- 4.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(8):1616–1626. doi: 10.1021/acs.chemrestox.5b00190. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 5.Jeffery J., Carradus M., Songin K., Pettit M., Pettit K., Wright C. Optimized method for determination of 16 FDA polycyclic aromatic hydrocarbons (PAHs) in mainstream cigarette smoke by gas chromatography-mass spectrometry. Chem. Cent. J. 2018;12(1):27. doi: 10.1186/s13065-018-0397-2. Epub 2018/03/15 PubMed PMID: 29536204. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6.Liu H., Sun S., Zong Y., Li P., Xie J. Analysis of hydrogen peroxide in cigarette smoke from selected Chinese cigarette brands under conventional and intense machine smoking conditions. Eur. Food Res. Technol. 2012;235(6):1107–1115. [Google Scholar]
- 7.Watson C.V., Valentin-Blasini L., Damian M., Watson C.H. Method for the determination of ammonium in cigarette tobacco using ion chromatography. Regul. Toxicol. Pharmacol. 2015;72(2):266–270. doi: 10.1016/j.yrtph.2015.04.019. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 8.Ticha J., Wright C. Rapid detection of toxic compounds in tobacco smoke condensates using high-resolution 1H-nuclear magnetic resonance spectroscopy. Anal. Methods. 2016;8(34):6388–6397. [Google Scholar]
- 9.Pazo D.Y., Moliere F., Sampson M.M., Reese C.M., Agnew-Heard K.A., Walters M.J. Mainstream smoke levels of volatile organic compounds in 50 U.S. Domestic cigarette brands smoked with the ISO and canadian intense protocols. Nicotine Tob. Res. 2016;18(9):1886–1894. doi: 10.1093/ntr/ntw118. Epub 2016/04/27 PubMed PMID: 27113015. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10.Marcilla A., Beltran M.I., Gómez-Siurana A., Berenguer D., Martínez-Castellanos I. Comparison between the mainstream smoke of eleven RYO tobacco brands and the reference tobacco 3R4F. Toxicol. Rep. 2014;1:122–136. doi: 10.1016/j.toxrep.2014.05.004. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11.Eldridge A., Betson T.R., Gama M.V., McAdam K. Variation in tobacco and mainstream smoke toxicant yields from selected commercial cigarette products. Regul. Toxicol. Pharmacol. 2015;71(3):409–427. doi: 10.1016/j.yrtph.2015.01.006. [DOI] [PubMed] [Google Scholar]
- 12.Belushkin M., Jaccard G., Kondylis A. Considerations for comparative tobacco product assessments based on smoke constituent yields. Regul. Toxicol. Pharmacol. 2015;73(1):105–113. doi: 10.1016/j.yrtph.2015.06.017. [DOI] [PubMed] [Google Scholar]
- 13.Inaba Y., Uchiyama S., Kunugita N. Spectrophotometric determination of ammonia levels in tobacco fillers of and sidestream smoke from different cigarette brands in Japan. Environ. Health Prev. Med. 2018;23(1):15. doi: 10.1186/s12199-018-0704-5. Epub 2018/04/29 PubMed PMID: 29703135; PubMed Central PMCID: PMCPMC5923008. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 14.Mueller D., Schulze J., Ackermann H., Klingelhoefer D., Uibel S., Groneberg D.A. Particulate matter (PM) 2.5 levels in ETS emissions of a Marlboro Red cigarette in comparison to the 3R4F reference cigarette under open- and closed-door condition. J. Occup. Med. Toxicol. 2012;7 doi: 10.1186/1745-6673-7-14. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.Piadé J.J., Jaccard G., Dolka C., Belushkin M., Wajrock S. Differences in cadmium transfer from tobacco to cigarette smoke, compared to arsenic or lead. Toxicol. Rep. 2015;2:12–26. doi: 10.1016/j.toxrep.2014.11.005. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16.Jaccard G., Tafin Djoko D., Moennikes O., Jeannet C., Kondylis A., Belushkin M. Comparative assessment of HPHC yields in the Tobacco Heating System THS2.2 and commercial cigarettes. Regul. Toxicol. Pharmacol. 2017;90:1–8. doi: 10.1016/j.yrtph.2017.08.006. [DOI] [PubMed] [Google Scholar]
- 17.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(3):201–207. doi: 10.7888/juoeh.39.201. Epub 2017/09/15 PubMed PMID: 28904270. [DOI] [PubMed] [Google Scholar]
- 18.Li X., Luo Y., Jiang X., Zhang H., Zhu F., Hu S. Chemical analysis and simulated pyrolysis of tobacco heating system 2.2 compared to conventional cigarettes. Nicotine Tob. Res. 2018 doi: 10.1093/ntr/nty005. nty005-nty. [DOI] [PubMed] [Google Scholar]
- 19.Forster M., Fiebelkorn S., Yurteri C., Mariner D., Liu C., Wright 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. doi: 10.1016/j.yrtph.2017.10.006. [DOI] [PubMed] [Google Scholar]
- 20.Schaller J.P., Keller D., Poget L., Pratte P., Kaelin E., McHugh D. 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(Suppl 2):S27–s47. doi: 10.1016/j.yrtph.2016.10.001. Epub 2016/10/23 PubMed PMID: 27720919. [DOI] [PubMed] [Google Scholar]
- 21.Pratte P., Cosandey S., Goujon Ginglinger C. Investigation of solid particles in the mainstream aerosol of the Tobacco Heating System THS2.2 and mainstream smoke of a 3R4F reference cigarette. Hum. Exp. Toxicol. 2017;36(11):1115–1120. doi: 10.1177/0960327116681653. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 22.Poynton S., Sutton J., Goodall S., Margham J., Forster M., Scott K. A novel hybrid tobacco product that delivers a tobacco flavour note with vapour aerosol (Part 1): product operation and preliminary aerosol chemistry assessment. Food Chem. Toxicol. 2019 doi: 10.1016/j.fct.2017.05.022. [DOI] [PubMed] [Google Scholar]
- 23.Uchiyama S., Noguchi M., Takagi N., Hayashida H., Inaba Y., Ogura H. Simple determination of gaseous and particulate compounds generated from heated tobacco products. Chem. Res. Toxicol. 2018;31(7):585–593. doi: 10.1021/acs.chemrestox.8b00024. [DOI] [PubMed] [Google Scholar]
- 24.Ito S., Ishimori K., Ishikawa S. Effects of repeated cigarette smoke extract exposure over one month on human bronchial epithelial organotypic culture. Toxicol. Rep. 2018;5:864–870. doi: 10.1016/j.toxrep.2018.08.015. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 25.Kim H.R., Lee J.E., Jeong M.H., Choi S.J., Lee K., Chung K.H. Comparative evaluation of the mutagenicity and genotoxicity of smoke condensate derived from Korean cigarettes. Environ. Health Toxicol. 2015;30 doi: 10.5620/eht.e2015014. Epub 2016/01/23 PubMed PMID: 26796893; PubMed Central PMCID: PMCPMC4722968. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 26.Takahashi Y., Kanemaru Y., Fukushima T., Eguchi K., Yoshida S., Miller-Holt J. Chemical analysis and in vitro toxicological evaluation of aerosol from a novel tobacco vapor product: a comparison with cigarette smoke. Regul. Toxicol. Pharmacol. 2018;92(Supplement C):94–103. doi: 10.1016/j.yrtph.2017.11.009. [DOI] [PubMed] [Google Scholar]
- 27.Wang H., Word B., Lyn-Cook L., Jr., Yang M., Hammons G., Lyn-Cook B. Cytotoxicity of chronic exposure to 4 cigarette smoke condensates in 2 cell lines. Int. J. Toxicol. 2015;34(2):182–194. doi: 10.1177/1091581815574349. Epub 2015/03/25 PubMed PMID: 25800266. [DOI] [PubMed] [Google Scholar]
- 28.Fowler K., Fields W., Hargreaves V., Reeve L., Bombick B. Development, qualification, validation and application of the Ames test using a VITROCELL® VC 10® smoke exposure system. Toxicol. Rep. 2018;5:542–551. doi: 10.1016/j.toxrep.2018.04.003. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 29.Antherieu S., Garat A., Beauval N., Soyez M., Allorge D., Garcon G. Comparison of cellular and transcriptomic effects between electronic cigarette vapor and cigarette smoke in human bronchial epithelial cells. Toxicol. In Vitro. 2017;45(Pt 3):417–425. doi: 10.1016/j.tiv.2016.12.015. Epub 2017/01/10 PubMed PMID: 28065790. [DOI] [PubMed] [Google Scholar]
- 30.Azzopardi D., Patel K., Jaunky T., Santopietro S., Camacho O.M., McAughey J. Electronic cigarette aerosol induces significantly less cytotoxicity than tobacco smoke. Toxicol. Mech. Methods. 2016;26(6):477–491. doi: 10.1080/15376516.2016.1217112. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 31.Breheny D., Adamson J., Azzopardi D., Baxter A., Bishop E., Carr T. A novel hybrid tobacco product that delivers a tobacco flavour note with vapour aerosol (Part 2): in vitro biological assessment and comparison with different tobacco-heating products. Food Chem. Toxicol. 2017;106(Pt A):533–546. doi: 10.1016/j.fct.2017.05.023. Epub 2017/06/10 PubMed PMID: 28595930. [DOI] [PubMed] [Google Scholar]
- 32.Haswell L.E., Baxter A., Banerjee A., Verrastro I., Mushonganono J., Adamson J. Reduced biological effect of e-cigarette aerosol compared to cigarette smoke evaluated in vitro using normalized nicotine dose and RNA-seq-based toxicogenomics. Sci. Rep. 2017;7(1) doi: 10.1038/s41598-017-00852-y. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 33.Ishikawa S., Matsumura K., Kitamura N., Ishimori K., Takanami Y., Ito S. Application of a direct aerosol exposure system for the assessment of biological effects of cigarette smoke and novel tobacco product vapor on human bronchial epithelial cultures. Regul. Toxicol. Pharmacol. 2018;96:85–93. doi: 10.1016/j.yrtph.2018.05.004. [DOI] [PubMed] [Google Scholar]
- 34.Jaunky T., Adamson J., Santopietro S., Terry A., Thorne D., Breheny D. Assessment of tobacco heating product THP1.0. Part 5: in vitro dosimetric and cytotoxic assessment. Regul. Toxicol. Pharmacol. 2018;93:52–61. doi: 10.1016/j.yrtph.2017.09.016. [DOI] [PubMed] [Google Scholar]
- 35.Malinska D., Szymański J., Patalas-Krawczyk P., Michalska B., Wojtala A., Prill M. Assessment of mitochondrial function following short- and long-term exposure of human bronchial epithelial cells to total particulate matter from a candidate modified-risk tobacco product and reference cigarettes. Food Chem. Toxicol. 2018;115:1–12. doi: 10.1016/j.fct.2018.02.013. [DOI] [PubMed] [Google Scholar]
- 36.Taylor M., Carr T., Oke O., Jaunky T., Breheny D., Lowe F. E-cigarette aerosols induce lower oxidative stress in vitro when compared to tobacco smoke. Toxicol. Mech. Methods. 2016;26(6):465–476. doi: 10.1080/15376516.2016.1222473. [DOI] [PubMed] [Google Scholar]
- 37.Thorne D., Larard S., Baxter A., Meredith C., Gaa M. The comparative in vitro assessment of e-cigarette and cigarette smoke aerosols using the gammaH2AX assay and applied dose measurements. Toxicol. Lett. 2016 doi: 10.1016/j.toxlet.2016.12.006. Epub 2016/12/15 PubMed PMID: 27965004. [DOI] [PubMed] [Google Scholar]
- 38.Crooks I., Neilson L., Scott K., Reynolds L., Oke T., Forster M. Evaluation of flavourings potentially used in a heated tobacco product: chemical analysis, in vitro mutagenicity, genotoxicity, cytotoxicity and in vitro tumour promoting activity. Food Chem. Toxicol. 2018 doi: 10.1016/j.fct.2018.05.058. [DOI] [PubMed] [Google Scholar]
- 39.Roemer E., Schramke H., Weiler H., Buettner A., Kausche S., Weber S. Mainstream smoke chemistry and in vitro and in vivo toxicity of the reference cigarettes 3R4F and 2R4F. Beitrage zur Tabakforschung International/ Contrib. Tob. Res. 2012;25(1):316–335. [Google Scholar]
- 40.Wong E.T., Kogel U., Veljkovic E., Martin F., Xiang Y., Boue S. Evaluation of the Tobacco Heating System 2.2. Part 4: 90-day OECD 413 rat inhalation study with systems toxicology endpoints demonstrates reduced exposure effects compared with cigarette smoke. Regul. Toxicol. Pharmacol. 2019 doi: 10.1016/j.yrtph.2016.10.015. [DOI] [PubMed] [Google Scholar]
- 41.Das A., Dey N., Ghosh A., Das S., Chattopadhyay D.J., Chatterjee I.B. Molecular and cellular mechanisms of cigarette smoke-induced myocardial injury: prevention by vitamin C. PLoS One. 2012;7(9) doi: 10.1371/journal.pone.0044151. Epub 2012/09/13 PubMed PMID: 22970172; PubMed Central PMCID: PMCPMC3435405. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 42.Olfert I.M., DeVallance E., Hoskinson H., Branyan K.W., Clayton S., Pitzer C.R. Chronic exposure to electronic cigarettes results in impaired cardiovascular function in mice. J. Appl. Physiol. (Bethesda, Md : 1985) 2018;124(3):573–582. doi: 10.1152/japplphysiol.00713.2017. Epub 2017/11/04PubMed PMID: 29097631; PubMed Central PMCID: PMCPMC5899271. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 43.Carter C.A., Misra M., Maronpot R.R. Tracheal morphologic and protein alterations following short-term cigarette mainstream smoke exposure to rats. J. Toxicol. Pathol. 2012;25(3):201–207. doi: 10.1293/tox.25.201. Epub 2012/09/19PubMed PMID: 22988338; PubMed Central PMCID: PMCPMC3434335. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 44.Phillips B.W., Schlage W.K., Titz B., Kogel U., Sciuscio D., Martin F. A 90-day OECD TG 413 rat inhalation study with systems toxicology endpoints demonstrates reduced exposure effects of the aerosol from the carbon heated tobacco product version 1.2 (CHTP1.2) compared with cigarette smoke. I. Inhalation exposure, clinical pathology and histopathology. Food Chem. Toxicol. 2018;116(Pt B):388–413. doi: 10.1016/j.fct.2018.04.015. Epub 2018/04/15 PubMed PMID: 29654848. [DOI] [PubMed] [Google Scholar]
- 45.Fujimoto H., Tsuji H., Okubo C., Fukuda I., Nishino T., Lee K.M. Biological responses in rats exposed to mainstream smoke from a heated cigarette compared to a conventional reference cigarette. Inhal. Toxicol. 2015;27(4):224–236. doi: 10.3109/08958378.2015.1027799. Epub 2015/05/15 PubMed PMID: 25969858. [DOI] [PubMed] [Google Scholar]
- 46.Choi S.J., Lee S.H., Lee S.J., Yang M.J., Lee K. Subchronic inhalation toxicity study of 3R4F reference cigarette smoke in rats. Mol. Cell. Toxicol. 2016;12(3):313–325. [Google Scholar]
- 47.Certificate of Analysis. 1R6F Certified reference Cigarettes; 2017. Center for Tobacco Reference Products UoK. [Google Scholar]
- 48.Hage A.N., Krause W., Mathues A., Krasner L., Kasten S., Eliason J.L. Comparing the effects of electronic cigarette vapor and cigarette smoke in a novel in vivo exposure system. J. Vis. Exp. 2017;(123) doi: 10.3791/55672. Epub 2017/06/02 PubMed PMID: 28570524. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 49.Przybyla R.J., Wright J., Parthiban R., Nazemidashtarjandi S., Kaya S., Farnoud A.M. Electronic cigarette vapor alters the lateral structure but not tensiometric properties of calf lung surfactant. Respir. Res. 2017;18(1):193. doi: 10.1186/s12931-017-0676-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 50.Reilly S.M., Goel R., Bitzer Z., Elias R.J., Foulds J., Muscat J. Effects of topography-related puff parameters on carbonyl delivery in mainstream cigarette smoke. Chem. Res. Toxicol. 2017;30(7):1463–1469. doi: 10.1021/acs.chemrestox.7b00104. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 51.Goel R., Trushin N., Reilly S.M., Bitzer Z., Muscat J., Foulds J. A survey of nicotine yields in small cigar smoke: influence of cigar design and smoking regimens. Nicotine Tob. Res. 2017 doi: 10.1093/ntr/ntx220. PubMed PMID: 29059441. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 52.Goel R., Bitzer Z.T., Reilly S.M., Bhangu G., Trushin N., Elias R.J. Effect of charcoal in cigarette filters on free radicals in mainstream smoke. Chem. Res. Toxicol. 2018;31(8):745–751. doi: 10.1021/acs.chemrestox.8b00092. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 53.CORESTA . 2018. CRM 86. Determination of Select Carbonyls in Tobacco and Tobacco Products by UHHPLC-MS/MS. [Google Scholar]
- 54.ISO. ISO-3308 . Ineternational Organization for Standardization; 2000. Routine Analytical Cigarette-Smoking Machine-Definitions and Standard Conditions. [Google Scholar]
- 55.ISO. ISO 20778 . 2018. Cigarettes-Routine Analytical Cigarette Smoking Machine-definitions and Standard Conditions With an Intense Smoking Regime. [Google Scholar]
- 56.ISO. ISO 3402 . 1999. Tobacco and Tobacco Products -- Atmosphere for Conditioning and Testing. [Google Scholar]
- 57.TobReg . WHO Technical Report Series; 2015. WHO Study Group on Tobacco Product Regulation: Report on the Scientific Basis of Tobacco Product Regulation. n. 989. [PubMed] [Google Scholar]
- 58.Health Canada . 2000. Canadian Ministry of Justice: Tobacco Reporting Regulations. SOR/200-273. Registration 2000-06-26. Part 3: Emissions From Designated Tobacco Products. [Google Scholar]
- 59.Oldham M.J., Haussmann H.J., Gomm W., Rimmer L.T., Morton M.J., McKinney W.J. Discriminatory power of standard toxicity assays used to evaluate ingredients added to cigarettes. Regul. Toxicol. Pharmacol. 2012;62(1):49–61. doi: 10.1016/j.yrtph.2011.11.018. [DOI] [PubMed] [Google Scholar]
- 60.Dolka C., Piadé J.J., Belushkin M., Jaccard G. Menthol addition to cigarettes using breakable capsules in the filter. Impact on the mainstream smoke yields of the health Canada list constituents. Chem. Res. Toxicol. 2013;26(10):1430–1443. doi: 10.1021/tx400146x. [DOI] [PubMed] [Google Scholar]
- 61.Piadé J.J., Wajrock S., Jaccard G., Janeke G. Formation of mainstream cigarette smoke constituents prioritized by the World Health Organization - yield patterns observed in market surveys, clustering and inverse correlations. Food Chem. Toxicol. 2013;55:329–347. doi: 10.1016/j.fct.2013.01.016. [DOI] [PubMed] [Google Scholar]
- 62.d’Andres S., Boudoux R., Renaud J.M., Zuber J. TSNA levels in the mainstream smoke of simplified blend prototypes. Beiträge zur Tabakforschung / Contrib. Tob. Res. 2003;20(5):331. [Google Scholar]
- 63.Gunduz I., Kondylis A., Jaccard G., Renaud J.M., Hofer R., Ruffieux L. Tobacco-specific N-nitrosamines NNN and NNK levels in cigarette brands between 2000 and 2014. Regul. Toxicol. Pharmacol. 2016;76:113–120. doi: 10.1016/j.yrtph.2016.01.012. [DOI] [PubMed] [Google Scholar]
- 64.Appleton S., Olegario R.M., Lipowicz P.J. TSNA levels in machine-generated mainstream cigarette smoke: 35 years of data. Regul. Toxicol. Pharmacol. 2013;66(2):197–207. doi: 10.1016/j.yrtph.2013.03.013. [DOI] [PubMed] [Google Scholar]
- 65.CORESTA . 2017. CRM 72. Determination of Tobacco Specific Nitrosamines in Tobacco and Tobacco Products by LC-MS/MS. [Google Scholar]
- 66.Edwards S.H., Rossiter L.M., Taylor K.M., Holman M.R., Zhang L., Ding Y.S. Tobacco-specific nitrosamines in the tobacco and mainstream smoke of U.S. commercial cigarettes. Chem. Res. Toxicol. 2017;30(2):540–551. doi: 10.1021/acs.chemrestox.6b00268. Epub 2016/12/22 PubMed PMID: 28001416. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 67.Jaccard G., Kondylis A., Gunduz I., Pijnenburg J., Belushkin M. Investigation and comparison of the transfer of TSNA from tobacco to cigarette mainstream smoke and to the aerosol of a heated tobacco product, THS2.2. Regul. Toxicol. Pharmacol. 2018;97:103–109. doi: 10.1016/j.yrtph.2018.06.011. [DOI] [PubMed] [Google Scholar]
- 68.Lang G., Vuarnoz A. Matrix-bound 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone in tobacco: quantification and evidence for an origin from lignin-incorporated alkaloids. J. Nat. Prod. 2015;78(1):85–92. doi: 10.1021/np500725a. [DOI] [PubMed] [Google Scholar]
- 69.Diekmann J., Douda M., Rustemeier K. Rapid and sensitive method for the determination of propylene oxide in cigarette mainstream smoke by gas chromatography-mass spectrometry. J. Chromatogr. Sci. 2006;44(1):32–34. doi: 10.1093/chromsci/44.1.32. [DOI] [PubMed] [Google Scholar]
- 70.Gaworski C.L., Oldham M.J., Coggins C.R. Toxicological considerations on the use of propylene glycol as a humectant in cigarettes. Toxicology. 2010;269(1):54–66. doi: 10.1016/j.tox.2010.01.006. Epub 2010/01/19 PubMed PMID: 20079797. [DOI] [PubMed] [Google Scholar]
- 71.IARC . IARC; Lyon: 1999. IARC Monographs on the Evaluation of the Carcinogenc Risk of Chemicals to Man. [Google Scholar]
- 72.IARC . IARC; Lyon: 1994. IARC Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Man. [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.