Lorillard
Chapter 8 Absorption of Smoke Constituents by Nonsmokers
Fields
- Author
- Brunnemann, K.D.
- Haley, N.J.
- Hoffmann, D.
- Haley, N.J.
- Type
- REPT, OTHER REPORT
- BIBL, BIBLIOGRAPHY
- CHAR, CHART/GRAPH/MAPS
- SCRT, SCIENTIFIC REPORT
- BIBL, BIBLIOGRAPHY
- Area
- SPEARS,ALEXANDER/OFFICE
- Site
- G65
- Request
- R1-037
- Named Organization
- Elisa
- Gc
- Hplc
- NCI, Natl Cancer Inst
- Ria
- Gc
- Named Person
- Ames
- Haley, N.J.
- Hoffmann, I.
- Lowrey
- Matsukura
- Repace
- Stadler, B.
- Yamasaki
- Haley, N.J.
- Date Loaded
- 18 Dec 2001
- Master ID
- 87808171/8434
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I
An interlaboratory comparison of data from 11 laboratories
in 6 countries has demonstrated that GC and RIA techniques can
reliably quantitate nicotine and cotinine in urine and plasma
samples. An excellent correlation of laboratory methods was
observed in plasma samples and in urine samples to which cotinine
had been added as a tracer. However, in urine samples without
tracer, the RIA values for cotinine were found to be slightly
higher than those observed by GC. This could be due to a cross
reaction of the antibody with another compound present in urine,
or the discrepancy could arise from a loss of urinary cotinine
during GC extraction. The former explanation is more likely to
apply here. All methods have led to perfect distinction between
nonsmokers and active smokers (26). Table 2 presents data from
model studies on the uptake of ETS by nonsmokers under acute
exposure conditions (27-30). The main purpose of these assays
was to develop the methodology for field studies and to compare
the uptake of nicotine from environments with various degrees of
pollution and different types of pollutants under controlled
conditions. It has been shown that the equilibrium of nicotine
between vapor phase and particulate phase of ETS depends greatly
on the concentration and pH of the emitted smokestream (31) and,
thus, influences the uptake of nicotine by inhalation.
After repeated exposure to ETS under controlled conditions,
such as twice daily 80-minute exposure on 3 consecutive days to
the diluted pollutants of 4 concurrently smoked cigarettes (32),
the measurements in 4 nonsmokers have shown that except for
nicotine in the saliva, the physiological fluids do not reflect
maximal concentrations of nicotine and cotinine until at least 24
hours later. This observation has led to comparisons of the
elimination of cotinine in smokers and nonsmokers exposed to ETS
(33). In the first study, the half-life (t1/2) of cotinine
elimination from plasma of smokers was 18.5 hours; in the case of
passive smokers, it was 49.7 hours. The corresponding
disappearance (tl/z)of cotinine from the urine took 21.9 hours
and 32.7 hours, respectively. In a second assay, five cigarette
smokers were asked to abstain from tobacco use for 5 days and
were then given nicotine gum for three days. After another 8
days of abstinence from nicotine, the volunteers were exposed to
sidestream smoke. At this point, the cotinine elimination (tj/Z)
from urine (ng/ml) by smokers took 15.4 hours, by nicotine gum
users 18.2 hours, by 8-day exsmokers 27.5 hours, and by the
never-smokers 25.6 hours (33). These findings suggest that the
residence times of nicotine, cotinine and other tobacco
alkaloids, are likely related to the route of nicotine uptake as
well as to possible differences in metabolism between smokers and
nonsmokers. The longer elimination time for cotinine in
nonsmokers has been confirmed by other study groups (35-37),
however, the observation has also been challenged (38,39). A
longer residence time of nicotine metabolites in nonsmokers could
conceivably increase the possibility of endogenous formation of
carcinogenic N-nitrosamines (40).
98

REFERENCES
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107

others (65) and also by a controlled chamber assay (61). One
study in which significant elevations of COHb were found used
controlled exposure to tobacco smoke at a level of 25 ppm CO for
8 hours. This intense exposure resulted in an average increase
of COHb levels by 2.5% (85). However, such results are not
applicable to free-living situations in field studies (67).
3. Thiocyanate. Smoke is detoxified in the liver to
thiocyanate (SCN-). Measurement of SCN- has been used to
differentiate smokers from nonsmokers or, as mentioned earlier,
in combination with nicotine-cotinine assays to distinguish
smokers from chewers of tobacco. Thiocyanate can also be derived
from the diet, cruciferous vegetables being an excellent source
(68). The specificity of SCN as a marker of tobacco smoke
inhalation is poor and it is generally difficult to distinouish
light smokers from nonsmokers. This lack of specificity makes
SCN- unsuitable for the evaluation of ETS uptake by nonsmoking
subjects.
4. Hydroxyproline. Japanese investigators have studied the
excretion of hydroxyproline in persons exposed to ETS as well as
in active smokers and in persons exposed to high levels of air
pollutants (69). The rationale for these studies is that the
inhalation of nitrogen dioxide causes degradation of lung
collagen and elastin which results in urinary excretion of
hydroxyproline. The investigations of the Japanese group
suggested an elevated excretion of hydroxyproline by children of
smoking parents as well as by wives of smoking husbands, active
smokers, and individuals exposed to vehicle emissions. Since NOx
levels in ETS are relatively low by comparison to mainstream
smoke or vehicle emissions (56,70,71), such increased elimination
of hydroxyproline in passively exposed persons seemed surprising.
In fact, another group of investigators has been unable to
confirm this finding (72). Additional investigations, under
controlled exposure conditions and field studies are needed
before this compound can be properly evaluated as a marker for
ETS uptake.
5. N-Nitroso-Amino Acids. The occurrence of endogenous
nitrosation reactions in cigarette smokers has been demonstrated
in several studies. This phenomenon entails the risk of
endogenous formation of carcinogenic N-nitrosamines. Endogenous
formation of N-nitrosamines has been proven by urinary excretion
of the noncarcinogenic N-nitrosoproline (NPRO), N-
nitrosothioproline (NTPRO), and N-nitrosomethylthioproline
(NNTPRO). Whereas the average excretion of NPRO in nonsmokers
amounted to 2.0±1.5 ug/24 hrs, cigarette smokers excreted an
average of 7.0±4.0 ug/24 hrs (73-77). In the case of NTPRO, the
average urinary excretion by nonsmokers (ug/24 hrs) was 5.9, that
by cigarette smokers 8.7 and that of NMTPRO was 5.6 and 8.5,
respectively (75). Only two studies have explored the
possibility that endogenous formation of N-nitrosamino acids may
102

B. Genotoxicity of Physiological Fluids
Several studies have explored the possibility that
physiological fluids of cigarette smokers contain significantly
higher amounts of genotoxic agents than those of nonsmokers (81).
The most extensive data base in this field has shown
significantly higher mutaqenicity in the Salmonella thvohimurium
assay of urine of cigarette smokers compared to those of
nonsmokers. Since the original study by Yamasaki and Ames in
1977 (83) at least 20 investigations have shown that the urine of
cigarette smokers is significantly more mutagenic than the urine
of nonsmokers w#o are not ex#osed to genotoxic agents in
occupational environments. But it has also been shown that the
mutagenicity of the urine of smokers can be effected by diet
(84). It has further been surmized that exposure of nonsmokers
to ETS may lead to increased urinary excretion of mutagens. Of
the 6 published studies in which the urine of passive smokers was
tested for mutagenicity with the Ames test, 3 showed increased
activity and 3 showed no increase or, at the most an
insignificant increase in mutagenic activity (81,85-87). It
appears likely that the presently widely used methodology by
Yamasaki and Ames (83) can be significantly refined (86,88).
This may then enable investigators to assay the urine of
involuntary smokers for their exposure to genotoxic agents or
their precursors due to exposure to ETS.
C. Adduct Formation of Carcinogens in Passive Smokers.
Measurements in physiological fluids of nicotine and its
major metabolite, cotinine, have been shown to be objective
indicators of the uptake of ETS. It appears also that, upon
refinement of the methodology, the assay for mutagenicity of the
urine will reflect the uptake of genotoxic ETS constituents by
nonsmokers. However, these assays will not reflect an
individual's response to specific ETS carcinogens. That
information is best obtained by assessing levels of
macromolecular adducts with carcinogens or their metabolites.
Development of such assays is based an examining the mechanisms
of metabolic activation and detoxification of tobacco smoke
carcinogens.
1. Benzo(a)pyrene. In the case of active smokers, adducts
of at least 4 types of tobacco carcinogens or procarcinogens have
been studied. These adducts are formed by reaction of specific
metabolites of tobacco smoke constituents with DNA and/or
hemoglobin. Benzo(a)pyrene (BaP), a carcinogenic representative
of the polynuclear aromatic hydrocarbons in tobacco smoke is
known to be metabolized to bay region diol epoxides (e.g. 7,8-
dihydroxy-9,10-epoxy-7,8,9,10-tetrahydroBaP). Such diol epoxides
can bind to DNA in human tissues and lymphocytes. Antibodies
developed against the major BPDE-DNA adduct have been used to
104

methylbutyramide. Methods Enzymol. 84: 628-640, 1982.
25. Gritz, E.R., Baer-Weiss, V., Benowitz, N.L., Van Vunakis, H.,
and Jarvik, M.E. Plasma nicotine and cotinine concentrations in
habitual smokeless tobacco users. Clin. Pharmacol. Ther. 30: 201-
205, 1981.
26. Biber, A., Scherer, G., Hoepfner, I., Adlkofer, F., Heller,
W.-D., Haddow, J.E., and Knight, G.J. Determination of nicotine
and cotinine in human serum and urine: an interlaboratory study.
Toxicol. Lett. 35: 45-52, 1987.
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Med. Wochenschr. 112: 2328-2334, 1970.
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Guillerme, R. Determination de la nicotine par chromatographie en
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Ingebrethsen, B.J. Studies on the vapor-particulate phase
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smoking under controlled conditions and the elimination of
cotinine. Proc. 4th International Conference on Indoor Air
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17,1987.
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Measuring the exposure of infants to tobacco smoke. New Engl. J.
Med. 310: 1075-1078, 1984.
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Absorption and elimination of nicotine by smokers, nonsmokers and
chewers of nicotine gum. In: The Pharmacology of Nicotine, Rand,
M.J. and Thurau, K., eds., IRL Press, Washington, DC, 1988, pp. 20-
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Haley, N.J. Elimination of urinary cotinine in children exposed
to known levels of sidestream cigarette smoke. Proc. 4th
109

48. Jarvis, M.J., Russell, M.A.H., Feyerabend, Eiser, J.R.,
Morgan, P., Gammage, P., and Gray, E.M. Passive exposure to
tobacco smoke: saliva cotinine concentrations in a representative
population sample of nonsmoking school children. Brit. Med. J.
291: 927-929, 1985.
49. Luck, W. and Nau, H. Nicotine and cotinine concentrations in
serum and urine of infants exposed via passive smoking or milk from
smoking mothers. J. Pedriatr. 107: 816-820, 1985.
50. Pattishall, E.N., Strope, G.L., Etzel, R.A., Helms, R.W.,
Haley, N.J., and Denny, F.W. Serum cotinine as a measure of
tobacco smoke exposure in children. Am. J. Dis. Children 139:1101-
1104, 1985.
51. Schwartz-Bickenbach, Schulte-Hobein, Abt, Plum, C., and Nau,
H. Smoking and passive smoking during pregnancy and early infancy:
effects on birth weight, lactation period, and cotinine
concentrations in mother's milk and infant's urine. Toxicol. Lett.
35: 73-81, 1987.
52. Sepkovic, D.W., Axelrad, C.M., Colosimo, S.G., and Haley, N.J.
Measuring tobacco smoke exposure: clinical applications and passive
smoking. Presented at the Both Ann. Mtq. Air Pollution Control
Association 1987, New York, NY, Abstr. 87-80-2, 1987.
53. Jarvis, M.J., McNeill, A.D., Russell, M.A.H., W4est, R.J.,
Bryant, A. and Feyerabend, C. Passive smoking in adolescents: One
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ill

95. Bryant, M.S., Skipper, P.L., Tannenbaum, S.R., and Maclure,
M. Hemoglobin adducts of 4-aminobiphenyl in smokers and
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115

12. Saxena, K. and Scheman, A. A suicide plan by nicotine
poisoning: A review of nicotine toxicity. Vet. Hum. Toxicol.
27: 495-497, 1985.
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Radioimmunoassay for nicotine and cotinine. IARC Sci. Publ. 81:
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plasma and saliva by liquid chromatography. Clin. Chem. 32: 979-
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electrochemical detection. LC-GC ¢: 53-55, 1988.
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Vunakis, H., and Langone, J.J. Stereospecific monoclonal
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immunosorbent assays. J. Immunol. Methods 90: 202-213, 1986.
21. Neurath, G.B., Duenger, M., Orth, D., and Pein, F.G.
trans-3'-hydroxycotinine as a main metabolite in urine of smokers.
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22. Neurath, G.B., Pein, F.G. Gas chromatographic determination
of trans-3'-hydroxycotinine, a major metabolite of nicotine in
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108

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Indoor air pollution by tobacco smoke: model studies on the uptake
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67. Scherer, G., Westphal, K., Hoepfner, I., Adlkofer, F., and
Sorsa, M. Biomonitoring of exposure to potentially mutagenic
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self-reported smoking behavior: biochemical analysis of cotinine
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The study on the relationship between urinary hydroxyproline and
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sidestream smoke. IARC: Sci. Publ. 81: 11-24, 1987.
112

assess its presence in surgical specimens of lung tissue, in
human placenta, and in peripheral blood lymphocytes (89-91).
Evidence for the presence of such adducts in samples from smokers
has been ascertained but significant differences between smokers
and nonsmokers have not been observed.
2. Aromatic Amines. 4-Aminobiphenyl and 2-naphthylamine
are the known tobacco smoke constituents which are most likely to
contribute to the increased risk of bladder cancer of cigarette
smokers. The mechanisms by which these compounds are
metabolically activated and produce DNA adducts in the bladder
epithelium have been extensively studied (92). These studies
have shown that the corresponding hydroxylamines are key
intermediates in DNA and protei-n modification. The
hydroxylamines also react with hemoglobin, in the case of 4-
aminobiphenyl, a sulfinic acid amide of the beta-cysteine (93-
95). This adduct.readily releases 4-aminobiphenyl upon treatment
with dilute acid. A method was developed to analyze the released
4-aminobiphenyl by gas chromatography with detection by negative
ion chemical ionization mass spectrometry (95). Application of
this method to smokers showed that adduct levels were higher than
in nonsmokers, and decreased upon smoking cessation. The method
may be further refined for assessing the uptake of carcinogenic
aromatic amines from ETS by nonsmokers.
3. Ethylene. This volatile unsaturated hydrocarbon is
present in both mainstream smoke (200-400 ug/cigarette) and
sidestream smoke of cigarettes (96). Cigarette smoke contains
also traces of the carcinogenic ethylene oxide (7.0 ug/cigarette;
97,98). Upon absorption, ethylene is metabolized to the reactive
ethylene oxide. The latter binds to cellular macromolecules and
to hemoglobin. The alkylated valine is cleaved off of the
isolated hemoglobin and the derivatized hydroxyethylvaline is
analyzed by GC-MS. Cigarette smokers showed significantly higher
hydroxyethylvaline levels (389±138 pg/g hemoglobin) than
nonsmokers (58±25 pg/g; 99). So far the method has not been
applied to estimates of exposure of involuntary smokers to the
procarcinogen ethylene.
4. Tobacco-Specific N-Nitrosamines. During tobacco
processing and during smoking tobacco alkaloids give rise to
tobacco-specific N-nitrosamines (TSNA). The nicotine-derived N-
nitrosamines N'-nitrosonornicotine (NNN) and 4-
(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK) are powerful
carcinogans. They occur in relatively high concentrations in
cigarette mainstream smoke (NNN, 0.12-3.7 ug/cigarette; NNK,
0.08-0.77 ug/cigarette) and sidestream smoke (NNN, 0.15-1.7
ug/cigarette; NNK, 0.2-1.4 ug/cigarette; 40). These agents are
metabolically activated by aipha-hydroxylation, leading to a
highly reactive intermediate which forms DNA adducts and protein
adducts (Fig. I). Metabolic activation of NNN and NNK also leads
to the formation of hemoglobin adducts. Acid or base hydrolysis
105
