Relationships between non-occupational cadmium exposure and expression of nine cytochrome P450 forms in human liver and kidney cortex samples1
Introduction
Remarkable inter-individual variations in abundance and activity of some human CYP forms have been reported [1], [2], [3], [4], [5], [6], [7]. For example, in one study [3] using a human liver bank of twenty-one samples (fourteen males, six females, and one unknown), the fold variations (number in parentheses) in catalytic activity found for each CYP were reported as follows: 1A2 (3), 2A6 (21), 2C9 (8), 2C19 (175), 2D6 (18), 2E1 (5), 3A4 (18). It is considered that such variation may be due to exposure to particular classes of drugs and compounds of endogenous and exogenous origin in some individuals [1], [3], [8], [9] and to genetically determined variation in CYP expression, since a number of genetic polymorphisms of human genes have been identified to contribute to variability in the abundance of the corresponding CYP proteins [10], [11], [12], [13], [14]. A recent study on genetic polymorphism reported striking differences in CYP1A1, 1B1, and 2D6 gene polymorphism in Caucasians and Japanese [13], [14].
Among the environmental factors that are important sources of CYP variability among individuals, cigarette smoke exposure has been subject to the most intense research. Results have shown that among the many chemicals in tobacco smoke, polycyclic aromatic hydrocarbons may be inducers of CYP1A2 in liver and CYP1A1 in lung and placenta in tobacco smokers [1], [8], [9]. Cadmium is another common environmental toxin found in low levels in cigarette smoke and in most foods [15], [16], [17], [18], [19], [20], [21], but the possible influence of environmental cadmium exposure on CYP expression and inter-individual variation has not been clarified.
In the non-occupationally exposed population, food and tobacco smoke are known to be major sources of cadmium [15], [16], [19], [22]. Cadmium intake in the range of 9–15 μg/day was estimated for an average Australian consumer, using data from the 1996 Market Basket Survey [21]. Potatoes, wheat, cocoa, and meat constitute 46%, 16%, 12%, and 7%, respectively of total cadmium intake. Crustaceans, liver, peanuts, and vegetables each constitute only 2–3% of cadmium in the diet, providing a further 11% to the total intake. Cadmium of dietary and tobacco smoke origin is known to accumulate in the tissues where CYP enzymes are found, including the placenta, although its accumulation in the proximal tubular cells of the kidney cortex appears to be most extensive [20], [22], [23], [24], [25], [26], [27], [28], which explains why kidney is a target for cadmium toxicity in the non-occupationally exposed population. Cadmium in the kidneys accounts for one-third of the total body cadmium burden, while cadmium in the placenta has been found to increase with age of mothers [27]. Cadmium in lung was found to derive mainly from cigarette smoke and from polluted air [22], [29].
The purpose of this present study was to reveal variations in the expression of selected CYP proteins in liver and kidney that may be attributable to human exposure to environmental cadmium, as reflected by levels of cadmium accumulated in liver and kidney cortex samples. Formulation of this hypothesis developed out of work by ourselves and others [30], [31], [32], [33], [34] showing changes in tissue CYP content associated with cadmium administration to rats and rabbits. Other variables were also taken into consideration in this analysis. These variables were donor age, gender, CYP2A6 genotype, levels of exposure to cigarette smoke, and liver histopathology, some of these being established to be a cause of inter-individual variation in CYP expression [35], [36], [37], [38], [39], [40], [41], [42], [43], [44]. The present paper focuses on the following CYP forms: CYP1A1, 1A2, 1B1, 2A6, 2C9, 2C8/19, 2D6, 3A4, and 3A5. Levels of these CYP forms in liver and kidney samples were determined by Western immunoblotting with a panel of polyclonal antipeptide antibodies possessing high specificity and which have previously been validated for use in studying CYP expression in human liver, lung and placenta tissues [1], [6], [8], [9].
Section snippets
Chemicals
Bovine liver standard (SRM 1577a) was purchased from the US National Institute of Standards (NST) and ICP multi-element standards were from EM Science. To achieve the highest purity possible, analytical grade HNO3 (69%, w/v) was distilled before use. All containers used in specimen collection and preparation were tested prior to their use to ensure they contained undetectable amounts of cadmium or were metal-free. The Qiagen DNeasy Tissue Extraction Kit was obtained from Qiagen Pty Ltd.,
Results
The sample group was composed of twenty-two males and six females with ages ranging from 3 to 89 years. Each individual’s age, gender, level of exposure to cigarette smoke, liver and kidney cadmium contents, and liver histopathology results are shown in Table 1. The overall mean age for the sample group was 42.5 years. The mean ages for males and females were not significantly different. The level of exposure to cigarette smoke of each subject was assessed as being high, medium, or low based
Discussion
In our attempt to document environmental sources of variation in human CYP expression, we elected to analyse CYP expression in the liver and kidney samples from people who died of accidental causes. This sample group was likely to include “apparently healthy” individuals and is the closest to a random sample of the general population since an accidental cause of death may be viewed as a random incident. Since disease and other host factors are also known to contribute to CYP expression,
Acknowledgements
We thank all staff of the John Tonge Centre for Forensic Sciences for their assistance in sample collection. We are grateful to Dr. Alan Greig in the ICP/MS laboratory in the Department of Earth Sciences for his analysis of tissue metal contents. We thank Professor Don Davies of Clinical Pharmacology section, University of London for his support. The National Research Centre for Environmental Toxicology was funded by the Australian National Health and Medical Research Council, Queensland
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Abbreviation: CYP, cytochrome P450.