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Tobacco and Public Health - TCSC Indonesia

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STEPHEN S. HECHT 105<br />

Table 5.2 (continued) NNAL <strong>and</strong> its glucuronides (NNAL-Gluc) in urine: biomarkers of NNK<br />

uptake<br />

Study group Main conclusions Reference<br />

7. 21 smokers <strong>and</strong> NNAL detected in amniotic fluid of 52.4% of (Milunsky et al. 2000)<br />

30 non-smokers smokers <strong>and</strong> 6.7% of non-smokers, a<br />

significant difference. NNAL levels in amniotic<br />

fluid of smokers, 0.025 ± 0.029 pmol/ml<br />

8. 12 smokers <strong>and</strong> NNAL <strong>and</strong> NNAL-Gluc not detected in follicular (Matthews et al. 2002)<br />

10 non-smokers fluid<br />

a Number <strong>and</strong> letter in parentheses represent number <strong>and</strong> gender of subjects.<br />

ETS, environmental tobacco smoke.<br />

in the urine of non-tobacco users unless they were exposed to ETS. Since NNAL is not<br />

present in cigarette smoke, the origin of NNAL <strong>and</strong> NNAL-Gluc in urine is metabolism<br />

of NNK. Most investigations to date demonstrate a correlation between NNAL<br />

plus NNAL-Gluc <strong>and</strong> cotinine, indicating that NNAL plus NNAL-Gluc is an effective<br />

biomarker of lung carcinogen (NNK) uptake, whereas cotinine is an effective biomarker<br />

of nicotine uptake. The NNAL-Gluc:NNAL ratio varies at least tenfold in smokers <strong>and</strong>,<br />

since NNAL-Gluc is a detoxification product whereas NNAL is carcinogenic, this ratio<br />

could be a potential indicator of cancer risk (Carmella et al. 1995; Richie et al. 1997). In<br />

human urine, (S)-NNAL-O-Gluc is the predominant diastereomer of NNAL-O-Gluc,<br />

while (S)-NNAL is slightly in excess over (R)-NNAL (Carmella et al. 1999). (S)-NNAL<br />

is the more tumorigenic enantiomer of NNAL in A/J mouse lung (Upadhyaya et al.<br />

1999). NNAL <strong>and</strong> NNAL-Gluc are only slowly released from the human body after<br />

smoking cessation, <strong>and</strong> this has been linked to particularly strong retention of<br />

(S)-NNAL, possibly at a receptor site (Hecht et al. 1999).<br />

Human uptake of carcinogens from ETS has been reviewed (Scherer <strong>and</strong> Richter<br />

1997). Levels of 1-HOP <strong>and</strong> hydroxyphenanthrenes in urine are not consistently<br />

increased by exposure to ETS, although small effects have been seen under some highexposure<br />

conditions (Hoepfner et al. 1987; Scherer et al. 1992, 2000; van Rooij et al.<br />

1994; Siwinska et al. 1999). All studies reported to date show significantly higher<br />

amounts of NNAL plus NNAL-Gluc, or NNAL-Gluc, in the urine of ETS-exposed<br />

humans than in unexposed controls (Table 5.2C, entries 1–5). In one study, uptake of<br />

NNK was over six times higher in women who lived with smokers compared to women<br />

who lived with nonsmokers (Anderson et al. 2001). In another investigation, widespread<br />

uptake of NNK was demonstrated in a group of economically disadvantaged<br />

schoolchildren (Hecht et al. 2001). As in smokers, a correlation between levels of<br />

cotinine <strong>and</strong> NNAL plus NNAL-Gluc in urine has been consistently observed in ETSexposed<br />

nonsmokers. The assay for NNAL <strong>and</strong> NNAL-Gluc in urine is ideally suited to<br />

investigations of ETS exposure, for two reasons. First, it has the required sensitivity to<br />

measure relatively low levels (typically about 0.05 pmol/ml urine). Secondly, since

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