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Dedication of the Symposium to
All speakers in th is symposium had the privilege of working
with Dr Bernard B. Brodie in his Laboratory of Chemical
Pharmacologyat the National Institutes of Health. We are
grateful to Dr Brodie for that memorable experience which
stimulated our interest in drug metabolism and the factors
that regulate it. Because of the many fundamental
contributions made by Dr Brodie to th is field, and because
of the impact Dr Brodie had on our own research, we
dedicate th is symposium to him. Th is dedication is
particularly appropriate because the symposium was held
on August 7, Dr Brodie's birthday.
Departm ent 0/Biochemistry and Drug Metabolism ,
N utley, New Jersey 07110. USA
College 0/Physician s and Surgeons,
Ne w York, New York 10032. USA
M em orial Sloan-Kettering Can cer Center,
New York, Ne w York 10021. USA
Uniform ed Services University ofthe Health Sciences,
Bethesda, Ma ryland 20014. USA
Ne w York, Ne w York 10021. USA
Individual differenees in the response of peop le to a drug and variability in the
response that oeeurs when patients are given a drug on several oeeasions are
Individuality in the responsiveness ofhumans to drugs and environmental ehemieaI s
is eaused , in part, by differenees in rates of ehemical biotransformations in different
effeets ofdietary faetors on the metabolism ofthese substanees in man are deseribed.
Interindividual differences in the metabolism offoreign chemieals
A number of years ago, the metabolism ofsome drugs and carcinogens by sampies of
human liver obtained during abdominal surgery was investigated. Variability in the
catalytic activity ofsampies from different individuals was found (Kuntzman, Mark,
Brand, Jacobson, Levin & Conney, 1966). More recent studies indicated marked
differences in the ability of liver sampies from different individuals to metabolize
benzo[a]pyrene, antipyrine, hexobarbitone, coumarin, aflatoxin BI, and
benzo[a]pyrene 7,8-dihydrodiol (Conney, Pantuck, Pantuck, Buening, Jerina,
Fortner, Alvares, Anderson & Kappas, 1979). Aflatoxin BI (a potent liver carcinogen)
and benzo[a]pyrene 7,8-dihydrodiol (a proximate carcinogenic metabolite of
benzo[a]pyrene) are both metabolized to chemically reactive metabolites by
microsomal enzymes before exerting their mutagenic and carcinogenic effects (Miller
& Miller, 1977a, 1977b; Conney, Levin, Wood, Yagi, Lehr & Jerina, 1978; Jerina,
Yagi , Thakker, Karle, Mah, Boyd, Gadaginamath, Wood, Buening, Chang, Levin &
Conney, 1978). A nine-fold difference in the metabolism of aflatoxin BI to mutagens
and a seven-fold difference in the metabolism of benzo[a]pyrene 7,8-dihydrodiol to
mutagens were observed among the ten liver sampies studied (Figure I). Similar
differences were observed in the metabolism of benzo[a]pyrene to phenolic
metabolites by the different liver sampies (Figure I). Individuality in the metabolism
ofbenzo[a]pyrene, benzo[a]pyrene 7,8-dihydrodiol, and aflatoxin BI to their reactive
metabolites may help explain individual differences in the sensitivity ofpeople to the
carcinogenic action ofthese chemicals.
Large interindividual differences occur for the metabolism of benzo[a]pyrene by
human placenta (Welch, Harrison, Conney, Poppers & Finster, 1968; Welch,
Harrison, Gommi, Poppers, Finster & Conney, 1969), cultured human skin (Levin,
Conney, Alvares, Merkatz & Kappas, 1972; Alvares, Kappas, Levin & Conney,
1973), human macrophages (Cantrell, Warr, Busbee & Martin, 1973), cultured
1974), bronchial cells (Harris, Autrup, Connor, Barrett, Mcfrowell & Trump, 1976;
Harris, Autrup, Stoner, Yang, Leutz, Gelboin, Selkirk, Connor, Barrett, Jones,
McDowell & Trump, 1977), and pancreatic duct cells (Harris et al., 1977). Large
interindividual differences also occur in the metabolism of dimethylhydrazine by
human colon explants (Autrup, Trump, Smith & Harris, 1980), and in the
metabolism of dimethylnitrosamine by human liver (Czygan, Greim, Garro,
Hutterer, Rudick, Schaffner & Popper, 1973). Although cigarette smoking markedly
stimulated benzo[a]pyrene hydroxylase activity in human placenta, there was a
70-fold difference in the enzyme activities ofplacentas from women who smoked the
same number ofcigarettes (Welch et a/., 1969). A 150-fold difference was observed for
the metabolism of benzo[a]pyrene to DNA-bound adducts by cultured bronchial
explants from different individuals (Harris, Autrup, Trump, McDowell, Apostolides
& Schafer , 1980), and a 100-fold difference was observed for the metabolism of
1,2-dimethylhydrazine to DNA-bound adducts by cultured colon explants from
different individuals (Autrup et al., 1980).
Studying the comparative metabolism of drugs and environmental carcinogens by
human liver in vitro is an approach for identifying drugs that are metabolized by the
same enzyme system(s) that metabolize(s) the carcinogen. The extent of first pass
metabolism or the half-life of a nontoxic drug that is metabolized by the same
enzyme system(s) that metabolize(s) an environmental carcinogen may serve as an
indirect index of an individual's ability to metabolize the carcinogen, and metabolic
studies with appropriate drugs may help to determine the potential hazard in
different individuals of exposure to the carcinogen. This approach for identifying
VARIABILITY IN HUMAN DR UG MET ABOLISM 53
3- 0H BP formed (pmol mg- I min-I)
Figure 1 Interindivid ual difTerenees in the metabolism of allatoxin B. benzo(a]pyrene
7,8-dihydrodiol and benzo(a]pyrene by mierosomes from sampies of human liver obtained
during abdominal surgery. All the liver sampies studied had normal histology. Metabolism of
benzo(a]pyrene to fluoreseent phenols and the metabolie aetivation of aflatoxin B, and
benzo[a)pyrene 7,8-dihydrodiol to rnutagens were measured. Taken from data by Conney eral.
individuals with an unusually high risk towards environmental carcinogens has been
summarized elsewhere (Conney, 1980).
Many exogenous chemieals such as drugs (Conney, 1967), alcohol (Misra, Lefevre,
Ishii, Rubin & Lieber, 1971; Iber, 1977), cigarette smoke (Pantuck, Kuntzman &
Conney, 1972; Pantuck, Hsiao, Maggio, Nakamura, Kuntzman & Conney, 1974;
Conney et al.. 1977), insecticides (Kolmodin, Azarnoff & Sjöqvist, 1969; Poland,
Smith, Kuntzman, Jacobson & Conney, 1970), polychlorinated biphenols (Alvares,
Fischbein, Anderson & Kappas, 1977), lead (Alvares, Kapelner, Sassa & Kappas,
1975; Alvares, Fischbein, Sassa , Anderson & Kappas, 1976b; Meredith, Campbell,
Moore & Goldberg, 1976) and certain dietary constituents (Alvares, Anderson,
Conney & Kappas, 1976a; Conney, Pantuck, Hsiao, Garland, Anderson, Alvares &
Kappas, 1976; Kappas, Anderson, Conney & Alvares, 1976; Kappas, Alvares,
Anderson, Pantuck, Pantuck, Chang & Conney, 1978; Pantuck, Hsiao, Conney,
Gariand, Kappas, Anderson & Alvares, 1976; Pantuck, Pantuck, Gariand, Min ,
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