A collaborative study among 20 participating laboratories was conducted for determination of phenols in mainstream cigarette smoke. The study resulted in establishment of CRM 78, ISO 23904, and ISO 23905 standardized methods.
2. Table 1. Participating laboratories and product volunteers.
Testing participants
Altria Client Services ITC Ltd.
ARISTA Laboratories ITG, France
BAT Souza Cruz SA – Brazil ITL – Reemtsma Cigarettenfabriken
British American Tobacco Japan Tobacco Inc.
China National Tobacco Corp. Beijing Cigarette Factory Japan Tobacco International
CNTC – Zhengzhou Tobacco Research Institute KT&G Corp.
CNTC QC Labstat International Inc.
Enthalpy Analytical, Inc. Philip Morris International – Brazil
Essentra Scientific Services Philip Morris International – Indonesia
Global Laboratory Services, Inc. R.J. Reynolds Tobacco Co.
Product Volunteers
British American Tobacco Germany GmbH Japan Tobacco – Japan
China National Tobacco Corp. Beijing Cigarette Factory Philip Morris International – Neuchatel, Switzerland
ITG Altadis Shanghai Tobacco Group Co. Ltd
Prozent der mittleren Ausbeute aus allen untersuchten
Produkten und beiden Abrauchprotokollen - lagen die
Werte zwischen 17 und 150%. Die größten Schwankungen
traten bei den Daten der Produkte mit der niedrigsten
“Teerausbeute”auf.Beiden Ergebnissen bestätigte sichdie
erwartete Tendenz in Bezug auf die Gesamtpartikelmasse,
denMischungstyp,dasProtokollunddierelative Analyten-
ausbeute. In diesemArtikel wird über Ergebnisse berichtet,
die für die Anwendung einer robusten Methode bei Hydro-
chinon, Resorcin, Catechin, Phenol, o-Kresol, m-Kresol
und p-Kresol sprechen und damit für die Einführung von
CRM 78 und standardisierten Methoden nach ISO 23904
und ISO 23905. [Contrib. Tob. Nicotine Res. 32 (2023)
18–25]
RESUME
Une étude conjointe rassemblant 20 laboratoires partici-
pants entendait concourir à la publication d’une recom-
mandation méthodologique concernant le dosage des
composés phénoliques dans la fumée principale de ciga-
rettes. Cette analyse reposa sur l’utilisation de 10 échan-
tillons pour essai incluant des cigarettes de référence et des
produits du commerce en provenance de différentes
régions (ISO 3308 Matière particulaire totale 1–16 mg/cig)
fumées suivant deux régimes de fumage (ISO 3308 et ISO
20778). La méthode T-114 de Santé Canada fut retenue en
guise de socle à la méthodologie analytique et donc, la
fumée principale de cigarette fut piégée dans des disques
filtrants en fibre de verre de 44-mm qui furent ensuite
soumis à une extraction par une solution d’acide acétique
à 1% en vue d’une analyse par chromatographie liquide à
haute performance(CLHP)avec détecteur de fluorescence.
Une analyse statistique fut réalisée conformément à la
norme ISO 5725 afin de générer des données de répétabili-
té (r) et de reproductibilité (R) relatives aux résultats
obtenus par machine à fumer linéaire et machine rotative.
Eu égard à la reproductibilité (R) exprimée en un pourcen-
tage du rendement moyen sur la totalité des produits
analysés et les deux régimes de fumage, les valeurs
oscillèrent entre 17 et 150%. Les produits présentant le
rendement en “goudron” le plus faible affichèrent les
données les plus variables. Les résultats évoluèrent dans la
plage de nos attentes concernant la matière particulaire
totale, le type de mélange, le régime de fumage et les
rendements relatifs de l’analyte. Les résultats étayant
l’emploi d’une méthode solide pour l’hydroquinone, le
résorcinol, le catéchol, le phénol, l’ o-crésol, l’ m-crésol et
le p-crésol sont présentés dans le présent article et appuient
l’établissement des méthodes normalisées CRM 78, ISO
23904 et ISO 23905. [Contrib. Tob. Nicotine Res. 32
(2023) 18–25]
INTRODUCTION
Smoking cigarettes is a cause of serious diseases in smok-
ers including lung cancer, heart disease, and emphysema.
Phenolic compounds catechol, hydroquinone, resorcinol,
phenol, and/or o-, m-, and p-cresol are often among harmful
and potentially harmful chemicals (HPHCs) of regulatory
interest (1–5).
Phenols have been measured by various methods at least
since the 1960s for research, product characterization, and
selective filtration purposes (6–13). In particular, Health
Canada’s T-114 was treated as a starting point for the study
reported here (14). The scope of T-114 is limited to pheno-
lic determination using intense smoking regime T-115 (15).
The purpose of this study was to establish a method with a
broader scope and to establish repeatability and
reproducibility estimates for the determination of phenolic
compounds using cigarettes and test pieces across a wide
range of “tar” yield and cigarette designs.
Thus, a collaborative study was conducted involving 20
laboratories from 11 countries, smoking 10 samples from
the world-wide market. The samples had a range of blend
styles (Virginia, American blend, and dark air-cured) and
ISO 3308 “tar” yields between 1 and 13 mg. The cigarettes
were smoked under both the ISO 3308 and ISO 20778
smoking regimes (16–17).
Statistical evaluations were made according to ISO 5725
recommendationsandrepeatabilityandreproducibilitydata
are provided (18).
19
CTNR @ 32 (1) @ 2023
3. Table 2. Study samples.
Sample ID Blend description
Approximate TPM ISO 3308 regime
(mg/cig) a
Approximate TPM ISO 20778 regime
(mg/cig)
CM7 Virginia 16.1 43.4
KR 1R5F American 2.0 31.8
KR 3R4F American 9.9 44.1
Sample 1 Dark air-cured 13.5 44.1
Sample 2 American 8.9 40.2
Sample 3 American 10.2 45.1
Sample 4 Virginia 4.0 30.3
Sample 5 Virginia 1.8 20.6
Sample 6 Virginia 11.3 36.1
Sample 7 Charcoal filtered 1.2 25.8
a
Based on the average TPM values from the study reported in this report
Table 3. Fluorescence detector settings.
Time initial Excitation (nm) Emission (nm)
0.0 280 310
12.4 280 310
12.5 274 298
23.0 274 298
24.0 280 310
28.0 280 310
Table 4. Elution program. a
Time (min)
Composition
% A % B
0 78 22
8 78 22
8.5 55 45
21 55 45
22 0 100
28 0 100
(Equilibrate 6 min)
a
Linear gradient
EXPERIMENTAL
Participating laboratories
The laboratories that conducted the testing along with the
product volunteers are listed in alphabetical order in
Table 1. To ensure anonymity of the results, each
laboratory was given a unique study code for data
exchange and reporting.
Study protocol
Participating laboratories were asked to follow a supplied
study protocol, a draft of a CORESTA Recommended
Method (CRM), and Health Canada T-114 (14) analytical
method for the determinationof phenols. Samples analyzed
for the study are listed in Table 2 with a range of blend and
cigarette designs that represent the market and a wide
range of total particulate matter (TPM) and analyte yields.
In accordance with the study protocol, participating
laboratories were asked to obtain reference cigarettes and
monitor test pieces directly from suppliers (19–20). Other
samples were commercial products from various regions
provided by the study volunteers listed in Table 1. Five
replicates of each product with each smoking regime were
requested to be generated. Reportable measures included
puff count, TPM, hydroquinone, resorcinol, catechol,
phenol, o-cresol, m-cresol, and p-cresol.
The yields of phenols collected under ISO 3308 (non-
intense) and ISO 20778 (intense) smoking regimes were
reported in units of microgram per cigarette (µg/cig) in the
templates provided to participants.
Smoke collection and sample preparation
Following the recommended method, conditioned ciga-
rettes were smoked using an automated 20-port constant
volumesmokingmachine, onto a conditioned, pre-weighed
glass fiber filter disc (pad).
TPM was determined gravimetrically and puff counts were
as recorded. The pads were extracted using 40 mL of 1%
aqueous acetic acid with 30 min of agitation using a wrist-
action shaker. Extracts were diluted using 1% acetic acid
based on total TPM. Samples below 15 mg TPM were
tested undiluted. Samples with 15–60 mg TPM were
diluted 2:5 and samples with 60–100 mg TPM were diluted
1:5 prior to analysis.
Analytical method
Samples were analyzed within 24 hours of collection and
extraction as hydroquinone is subject to rapid oxidation.
Samples were analyzed using high performance liquid
chromatography with selective fluorescence detection
(HPLC-FLD).
Detector settings are included in Table 3.
The mobile phase consisted of: 1% acetic acid (HOAC)
(aqueous; solvent A); 1% HOAC (in methanol; solvent B)
with a flow rate of 0.8 mL/min and an elution gradient as
noted in Table 4.
Sample injection volume was 10 µL to 20 µL onto a
pentafluorophenylpropyl analytical column (4.6 mm ×
150 mm × 3 µm).
20 CTNR @ 32 (1) @ 2023
4. Data analysis
Data consistency was verified using graphical and
numerical outlier detection techniques. Mandel’s h
plot and Grubbs test were used to evaluate between-
laboratories consistency.
Mandel’s k plot and Cochran’s test were used to
evaluate within-laboratory consistency. Grubbs and
Cochran tests are less likely to qualify data points as
outliers than their corresponding graphical methods
and to avoid excessive data exclusion. Thus, the final
decision on straggling (0.95) and outlying (0.99) data
was made using Cochran’s and single-iteration Grubbs
tests.
Straggling data were retained in the dataset but out-
lying data were removed for descriptive statistics
reporting. Overall mean, standard deviation, repeat-
ability (r), and reproducibility (R) values were deter-
mined according to ISO 5725-216 (18).
RESULTS AND DISCUSSION
Study design
The study design allowed for evaluation of the
robustness of the method across the linear range for
analytes of interest and confirmed the method’s
effectiveness with a variety of products.
Thus, the study samples chosen represented a wide
variety of TPM yields, tobacco blends, and product
construction parameters including varied filter
ventilation level and inclusion of a filter additive for
one study sample. Non-intense and intense smoking
regimes were used to verify applicability with the
recommended method.
General trending
Smoking related measures, including puff count and
TPM, had low variability for both smoking regimes
and across all products. Sample 7 (activated charcoal
filter and high filter ventilation) showed the highest
variability among the products tested. Additionally, no
significant differences in results were noted based on
choice of smoking machine type (i.e., linear or rotary).
The method appears to distinguish samples appropri-
ately. As expected of particulate phase and pad-
trapped semi-volatile constituents, the analyte yields
were directly correlated to TPM yields. When normal-
ized to TPM, phenols showed predictable trending
based on blend type. For example, Virginia (i.e., flue-
cured) products had higher phenolic:TPM values
compared to American blend samples containing
Burley tobacco.
In general, CM7 had the highest phenolic:TPM values.
This is consistent with previous research indicating
that flue-cured tobacco may generate higher levels of
some phenolic HPHCs (10, 21).
Data below the limits of quantification (LOQ)
Several data sets included non-numeric (i.e., < LOQ)
reporting for resorcinol, phenol, and the cresol compounds.
These values were excluded from outlier evaluation and
calculation of descriptive statistics and repeatability (r), and
reproducibility (R) values.
Outlier detection
Results of graphical outlier detection methods (Mandel’s h
and k plots) are not displayed in this report. During the first
iteration, there were 10 stragglers and 8 outliers for the non-
intense regime, and 13 stragglers and 7 outliers for the
intense regime. A second iteration of the test did not reveal
any further outliers. Grubbs single outlier test was employed
on the lab means and identified the following outliers and
stragglers. There were 4 stragglers and 8 outliers in the non-
intense regime, and 10 stragglers and 13 outliers for the
intense regime. All outliers were removed from the dataset.
All straggling data was retained.
Determination of inter-laboratory repeatability and repro-
ducibility variance
Mean, r, and R results with outliers removed are displayed
in Table 5 and Table 6. Values are typically above limits
established in ISO 8243 (22) for “tar”, nicotine, and carbon
monoxide (TNCO). This is not unexpected given the much
lower levels for phenols (µg) than TNCO measures (mg).
Additionally, the highest values for r and R noted in the
study were for results near LOQ at limits of the method’s
capabilities.
CONCLUSION
Through this study, a robust method CRM Nº 78 (23) and
ISO standards ISO 23904 (24) and ISO 23905 (25) were
established for the determination of mainstream cigarette
smoke phenolics.
The scope of the study included 20 laboratories testing 10
cigarette samples across a range of blends types. The
products tested included a range of TPM values between
1 mg and 16 mg (ISO 3308) and 32 mg and 51 mg (ISO
20778) and two smoking machine designs. The analytes
tested were from a 4-fold to a 60-fold range in of the
analytesofinterest.Reproducibility(R)values,expressedas
a percentage of mean yield, ranged from 17–150%.
ACKNOWLEDGEMENTS
The authors wish to acknowledge Steve Purkis, Michael
Intorp, and the participating laboratories and product
volunteers noted in Table 1. Without the work and support
provided, the objectives of the CORESTA Smoke Analytes
subgroup and this project could not have been completed.
21
CTNR @ 32 (1) @ 2023
5. Table 5. Non-intense smoking regime – Inter-laboratory mean yields, repeatability (r) and reproducibility (R) data.
CM7 1R5F 3R4F Sample 1 Sample 2 Sample 3 Sample 4 Sample 5 Sample 6 Sample 7
Puff count Mean a
8.45 6.90 8.28 5.66 7.88 6.91 5.19 4.54 6.82 6.16
STD b
0.35 0.27 0.33 0.27 0.36 0.34 2.35 1.10 1.65 0.25
TPM Mean 16.12 1.96 9.85 13.46 8.85 10.24 3.26 1.69 10.64 1.17
STD 1.07 0.32 0.78 1.78 0.75 0.84 1.71 0.52 2.90 0.31
Hydroquinone Mean 91.82 8.45 32.84 42.78 36.98 46.88 20.38 * 9.30 46.69 8.09
STD 7.47 1.33 2.78 3.85 3.43 3.60 3.26 1.19 4.08 0.96
r c
12.14 1.58 4.27 8.92 5.97 6.72 2.89 1.78 6.31 1.41
R d
23.58 3.97 8.67 13.40 10.99 11.75 9.49 3.68 12.73 2.97
N e
18 17 18 14 18 18 14 18 16 18
Resorcinol Mean 1.79 * 0.13 * 0.63 * 0.66 * 0.80 * 0.97 * 0.51 0.35 1.19 * 0.12 *
STD 0.30 0.04 0.15 0.21 0.16 0.18 0.09 0.05 0.21 0.03 *
r 0.52 0.09 0.19 0.37 0.29 0.29 0.18 0.14 0.22 0.10
R 0.95 0.14 0.46 0.67 0.51 0.58 0.30 0.17 0.63 0.13
N 17 13 15 12 16 16 13 15 15 12
Catechol Mean 96.39 8.13 36.77 35.30 39.87 42.61 24.17 12.89 58.19 7.84
STD 4.13 0.62 1.72 1.53 2.45 2.16 2.41 0.68 3.09 0.59
r 13.39 1.60 5.02 7.32 6.84 4.91 4.77 1.98 7.58 1.88
R 16.65 2.25 6.60 7.83 9.19 7.46 7.99 2.61 11.00 2.35
N 18 17 18 14 18 17 15 18 16 18
Phenol Mean 27.60 * 0.93 7.06 19.97 9.64 12.47 4.58 1.21 * 13.91 0.49 *
STD 2.94 0.19 0.80 1.49 1.28 1.15 1.11 0.25 1.42 0.11
r 4.17 0.44 1.59 4.12 2.43 2.52 1.24 0.36 3.04 0.29
R 9.05 0.65 2.64 5.57 4.20 3.93 3.30 0.77 4.81 0.39
N 16 14 18 14 18 18 15 16 16 13
o-Cresol Mean 5.63 0.38 2.33 5.75 2.62 3.30 1.34 0.42 * 3.40 0.21
STD 0.68 0.08 0.27 0.65 0.37 0.35 0.26 0.10 0.43 0.07
r 0.96 0.15 0.54 1.22 0.63 0.67 0.29 0.15 0.66 0.12
R 2.08 0.25 0.90 2.11 1.18 1.14 0.78 0.31 1.35 0.23
N 18 15 18 14 18 18 15 16 16 13
m-Cresol Mean 4.57 0.32 1.83 3.73 2.03 2.50 1.10 0.38 2.78 0.24
STD 0.67 0.10 0.18 0.45 0.33 0.29 0.22 0.07 0.28 0.12
r 0.69 0.12 0.37 0.77 0.42 0.43 0.23 0.11 0.53 0.10
R 1.98 0.29 0.61 1.43 0.99 0.90 0.64 0.23 0.92 0.36
N 17 13 17 13 17 17 14 17 16 13
p-Cresol Mean 12.45 0.73 4.56 10.40 5.44 6.49 2.49 0.88 6.25 0.44
STD 1.24 0.14 0.51 0.87 0.71 0.60 0.50 0.13 0.73 0.13
r 1.63 0.27 0.75 2.24 1.19 1.07 0.47 0.20 1.02 0.16
R 3.76 0.46 1.58 3.16 2.26 1.93 1.47 0.40 2.24 0.39
N 17 16 17 13 17 17 14 17 16 17
a
Mean: mean yield (μg/cig) except TPM (mg/cig) and puff count (pc)
b
STD: overall standard deviation
c
r: repeatability (μg/cig at 95% confidence interval)
d
R: reproducibility (μg/cig at 95% confidence interval)
e
N: number of datasets used for r and R determination after removal of outliers and non-quantifiable values
* Values calculated after removal of outlier (s)
22 CTNR @ 32 (1) @ 2023
6. Table 6. Intense smoking regime – Inter-laboratory mean yields, repeatability (r) and reproducibility (R) data.
CM7 1R5F 3R4F Sample 1 Sample 2 Sample 3 Sample 4 Sample 5 Sample 6 Sample 7
Puff count Mean a
11.78 6.40 10.39 7.00 9.74 7.62 5.81 5.02 9.31 6.54
STD b
0.56 0.36 0.51 0.40 0.51 0.52 2.63 1.25 2.33 0.37
TPM Mean 43.36 31.83 44.12 44.11 40.16 45.09 24.62 19.43 33.86 25.79
STD 6.09 4.07 3.97 4.80 4.62 4.87 12.32 5.91 9.33 3.76
Hydroquinone Mean 191.17 53.41 89.62 91.44 101.85 114.04 76.44 * 43.56 106.50 60.19
STD 15.16 5.08 7.49 7.99 8.60 6.30 5.32 4.30 9.49 5.47
r c
27.40 11.85 11.67 18.19 15.75 18.27 9.98 9.36 15.97 17.18
R d
49.02 17.74 23.43 27.67 27.88 24.05 17.37 14.67 30.16 21.70
N e
18 17 18 14 18 18 14 18 16 18
Resorcinol Mean 3.77 1.07 * 1.87 * 1.35 * 2.55 2.77 2.21 2.07 2.70 1.46
STD 0.79 0.15 0.40 0.41 0.68 0.79 0.48 0.44 0.39 0.42
r 0.70 0.38 0.45 0.60 0.65 0.75 0.80 0.68 0.71 0.57
R 2.31 0.55 1.18 1.27 1.99 2.32 1.52 1.39 1.26 1.27
N 18 14 15 11 17 18 15 17 16 17
Catechol Mean 198.81 41.73 90.24 76.29 100.18 96.21 79.79 * 54.38 127.00 * 51.10
STD 15.11 3.55 6.71 6.52 7.92 9.10 6.22 4.56 6.48 5.27
r 27.35 9.81 14.58 14.03 14.46 20.19 11.53 12.81 24.78 13.13
R 48.87 13.26 22.87 22.16 25.68 31.23 20.24 17.16 28.64 18.86
N 18 17 18 14 18 18 14 18 15 18
Phenol Mean 43.05 8.20 13.13 36.65 16.99 19.19 12.00 6.64 19.33 * 6.93
STD 3.59 0.91 1.05 1.20 1.46 1.59 1.33 0.63 1.35 0.57
r 8.93 1.88 3.30 8.39 4.14 4.82 2.96 1.74 4.59 3.13
R 12.83 3.05 4.17 8.22 5.51 6.21 4.56 2.34 5.58 3.23
N 18 17 18 14 18 18 15 18 15 18
o-Cresol Mean 8.67 2.53 4.15 10.88 4.66 5.22 3.14 * 1.90 4.53 * 1.97
STD 1.14 0.28 0.50 0.99 0.60 0.60 0.38 0.22 0.41 0.28
r 1.89 0.58 0.96 2.52 1.05 1.22 0.66 0.52 1.15 0.91
R 3.62 0.93 1.64 3.58 1.93 2.01 1.22 0.78 1.55 1.13
N 18 16 18 14 18 18 14 17 15 17
m-Cresol Mean 7.08 1.78 3.25 7.14 3.58 3.90 2.65 1.58 3.91 1.67
STD 1.07 0.22 0.45 0.74 0.51 0.37 0.43 0.22 0.37 0.35
r 1.27 0.48 0.72 1.49 0.68 0.90 0.64 0.45 0.84 0.69
R 3.22 0.76 1.42 2.47 1.55 1.31 1.34 0.74 1.28 1.16
N 17 16 17 13 17 16 14 17 16 17
p-Cresol Mean 20.16 * 5.53 8.54 * 21.25 9.99 * 10.77 * 6.49 4.14 9.08 * 4.12 *
STD 2.21 0.72 0.72 2.32 1.10 1.06 0.81 0.36 0.82 0.40
r 3.58 1.09 1.78 4.29 1.98 2.19 1.31 0.91 1.84 1.82
R 6.97 2.24 2.56 7.55 3.56 3.55 2.56 1.30 2.82 1.98
N 16 16 16 13 16 16 14 17 15 16
a
Mean: mean yield (μg/cig) except TPM (mg/cig) and puff count (pc)
b
STD: overall standard deviation
c
r: repeatability (μg/cig at 95% confidence interval)
d
R: reproducibility (μg/cig at 95% confidence interval)
e
N: number of datasets used for r and R determination after removal of outliers and non-quantifiable values
* Values calculated after removal of outlier (s)
REFERENCES
1. U.S. Food and Drug Administration: Harmful and
Potentially Harmful Constituents in Tobacco Products
and Tobacco Smoke; Established List; Fed Regist.
2012;77:20034–20037. Available at: https://www.
federalregister.gov/documents/2012/04/03/2012-772
7/harmful-and-potentially-harmful-constituents-in-
tobacco-products-and-tobacco-smoke-established-list
(accessed February 2023)
2. Rodgman, A. and T.A. Perfetti: The Chemical Compo-
nents of Tobacco and Tobacco Smoke; CRC Press, 2nd
Edition, Boca Raton, FL, USA (2013).
3. The Peoples Republic of China, The State Council:
State Tobacco Monopoly Administration. Available at:
https://english.www.gov.cn/state_council/2014/10/01/
23
CTNR @ 32 (1) @ 2023
7. content_281474991089748.htm (accessed February
2023)
4. Health Canada, Minister of Health: Tobacco Reporting
Regulations, SOR/2000-273. Available at:
https://laws-lois.justice.gc.ca/PDF/SOR-2000-273.p
df.2000 (accessed February 2023)
5. World Health Organization, WHO Study Group on
Tobacco Product Regulation: Report on the Scientific
Basis of Tobacco Product Regulation: Eighth Report
of a WHO Study Group; Technical Report Series
1029; World Health Organization, Geneva, Switzer-
land (2021). ISBN: 9789240022720
6. Carruthers, W. and R. Johnstone: Some Phenolic
Constituents of Cigarette Smoke; Nature 185 (1960)
762–763. DOI: 10.1038/185762a0
7. Spears, A.: Selective Filtration of Volatile Phenolic
Compounds from Cigarette Smoke; Tob. Sci. 7 (1963)
76–80. Available at: https://www.coresta.org/sites/
default/files/abstracts/Tobacco_Science_1963_7-17_
p._76-80_ISSN.0082-4523.pdf (accessed February
2023)
8. Smith, C.J., T.A. Perfetti, M.J. Morton, A. Rodgman,
R. Garg, C.D. Selassie, and C. Hansch: The Relative
Toxicity of Substituted Phenols Reported in Cigarette
Mainstream Smoke; Toxicol. Sci. 69 (2002) 265–278.
DOI: 10.1093/toxsci/69.1.265
9. Vaughan, C., S.B. Stanfill, G.M. Polzin, D.L. Ashley,
and C.H. Watson: Automated Determination of Seven
Phenolic Compounds in Mainstream Tobacco Smoke;
Nicotine Tob. Res. 10 (2008) 1261–1268.
DOI: 10.1080/14622200802123146
10. Dyakonov, A.J., R.T. Walker, and C.A. Brown:
Studies of the Formation of Smoke Phenols; Beitr.
Tabakforsch. Int. 23 (2008) 68–84.
DOI: 10.2478/cttr-2013-0850
11. Jiang, W., J. Wu, J. Shen, W. Liu, W. Xiao, L. Xu, J.
Sun, and Y. Zhang: Effect of Polylactic Acid (PLA)
Filter on Mainstream Cigarette Smoke and Deliveries
of Phenol; Paper ST18, presented at CORESTA
Smoke Science and Product Technology Joint Study
Groups Meeting, 2016, Berlin, Germany. Available at:
https://www.coresta.org/sites/default/files/abstracts/
2016_ST18_JiangWen.pdf (accessed February 2023)
12. Wilkinson, P.: A Preliminary Comparison of Fla-
voured Waterpipe Tobacco Aerosol with Cigarette
Smoke – Part 2: Hoffmann Analytes Machine Derived
Data; Poster STPOST 25, presented at CORESTA
Smoke Science and Product Technology Joint Study
Groups Meeting, 2019, Hamburg, Germany. Available
at:https://www.coresta.org/sites/default/files/abstracts/
2019_STPOST25_Wilkinson.pdf (accessed February
2023)
13. Jin, X.C., T.J. Hurst, and K.A. Wagner: Optimized
Method for Determination of Selective Phenolic
Compounds in Cigarette and Cigar Smoke by
UHPLC-FLD; Paper ST38, presented at CORESTA
Smoke Science and Product Technology Joint Study
Groups Meeting, 2019, Hamburg, Germany. Available
at: https://www.coresta.org/abstracts/optimized-
method-determination-selective-phenolic-compounds
-cigarette-and-cigar-smoke-0 (accessed February
2023)
14. Health Canada: Test Method T-114. Determination of
Phenolic Compounds in Mainstream Tobacco Smoke;
1999. Available at: https://health.canada.ca/apps/open
-information/tobacco/100PDF/T-114E.PDF (accessed
February 2023)
15. Health Canada: Test Method T-115. Determination of
“Tar”, Nicotine and Carbon Monoxide in Mainstream
Tobacco Smoke; 1999. Available at: https://health.
canada.ca/apps/open-information/tobacco/100PDF/
T-115E (accessed February 2023)
16. International Organization for Standardization (ISO):
ISO 3308:2012 Routine Analytical Cigarette-Smoking
Machine - Definitions and Standard Conditions; ISO,
Geneva, Switzerland, 2012. Available at:
https://www.iso.org/standard/60404.html (accessed
March, 2023)
17. International Organization for Standardization (ISO):
ISO 20778:2018 Cigarettes - Routine Analytical
Cigarette Smoking Machine - Definitions and Standard
Conditions With an Intense Smoking Regime; ISO,
Geneva, Switzerland, 2018. Available at:
https://www.iso.org/standard/69065.html (accessed
March, 2023)
18. International Organization for Standardization (ISO):
ISO 5725-2:2019. Accuracy (Trueness and Precision)
of Measurement Methods and Results – Part 2: Basic
Method for the Determination of Repeatability and
Reproducibility of a Standard Measurement Method;
2019, ISO, Geneva, Switzerland. Available at:
https://www.iso.org/standard/69419.html (accessed
February 2023)
19. University of Kentucky, College of Agriculture:Center
for Tobacco Reference Products. Available at:
https://ctrp.uky.edu/home (accessed February 2023)
20. Cooperation Centre for Scientific Research Relative to
Tobacco (CORESTA): CORESTA Monitors;
CORESTA, Paris, France. Available at: https://www.
coresta.org/coresta-monitors (accessed February 2023)
21. Davis, M.F., H.D. Mills, and S.C. Moldoveanu: Forma-
tion of Dihydroxybenzenes in Cigarette Smoke. Part 1.
Contribution from Chlorogenic Acid and Rutin; Beitr.
Tabakforsch. Int. 25 (2012) 396–408.
DOI: 10.2478/cttr-2013-0918
22. International Organization for Standardization (ISO):
ISO 8243:2013. Cigarettes – Sampling; 2019, ISO,
Geneva, Switzerland. Available at https://www.iso.
org/standard/60154.html (accessed February 2023)
23. Cooperation Centre for Scientific Research Relative to
Tobacco (CORESTA): CORESTA Recommended
Method No. 78 – Determination of Selected Phenolic
Compounds in Mainstream Cigarette Smoke by
HPLC-FLD; 2018, CORESTA, Paris, France. Avail-
able at: https://www.coresta.org/sites/default/files/
technical_documents/main/CRM_78-Dec2018.pdf
(accessed February 2023)
24. International Organization for Standardization (ISO):
ISO 23904. Cigarettes – Determination of Selected
Phenolic Compounds in Cigarette Mainstream Smoke
with an Intense Smoking Regime using HPLC-FLD;
2020, ISO, Geneva, Switzerland. Available at:
https://www.iso.org/standard/77341.html (accessed
February 2023)
24 CTNR @ 32 (1) @ 2023
8. 25. International Organization for Standardization (ISO):
ISO 23905. Cigarettes – Determination of Selected
Phenolic Compounds in Cigarette Mainstream Smoke
Using HPLC-FLD; 2020, ISO, Geneva, Switzerland.
Available at: https://www.iso.org/standard/77342.html
(accessed February 2023)
Corresponding author:
Rana Tayyarah
Labstat International Inc.
Kitchener
Ontario
Canada
E-mail: rana.tayyarah@labstat.com
25
CTNR @ 32 (1) @ 2023