Effect of strain and diet upon constitutive and chemically induced activities of several xenobiotic-metabolizing enzymes in rats
Introduction
The response of animals to administered chemicals in toxicity studies reflects a complex interaction of a number of variables, some intrinsic to a particular study design and others resulting from the treatment itself. Most studies on the impact of experimental variables upon functional changes in key enzymes and genotoxic or pathological endpoints reported to-date have been designed to evaluate effects of a single variable under tightly controlled conditions. However, hazard identification studies often involve a more complex and less controlled scenario. Commonly encountered variables include the use of different strains, dietary regimens, reduced feed intake, and/or primary and secondary effects of test materials or metabolites. It has long been accepted that these factors may affect the metabolism and pharmacokinetics and subsequent adaptation to and toxicity of administered test materials (Bidlack et al., 1986; Campbell and Hayes, 1975; Conney, 1967; Ioannides, 1999; Ronis and Ingelman-Sundberg, 1999). In particular, alterations in the activities of several so-called Phases I and II drug metabolizing enzymes have the potential to alter the toxicity of a wide range of xenobiotics. The numerous mixed-function oxygenases (MFO) comprising most of the Phase I enzymes metabolize and are often induced by a number of chemicals. The conjugative enzymes that comprise most of the Phase II enzymes are critical to the detoxification of many xenobiotics but also the activation of others, may also undergo at least limited substrate-induced increases in activity. The net effects of these changes are believed to dictate the body burden and to a large extent subsequent systemic toxicity of test materials undergoing hazard evaluation.
The objective of this study was to evaluate the influences of strain and diet upon constitutive and benzo(a)pyrene (B(a)P) induced activities of several hepatic Phases I and II enzymes in a multifactoral study design. This study was undertaken to complement gene expression profiles utilizing the same groups of animals (Kan et al., 2003).
Section snippets
Test materials
Benzo(a)pyrene (97% purity) and all biochemicals used in enzyme assays were purchased from Sigma Chemical (St. Louis, Missouri).
Animals and in-life data collection
Male and female CDF (Fischer 344)/CrlBR and Crl:CD (SD)BR rats were purchased from Charles River Laboratories (Raleigh, North Carolina and Portage, Michigan, respectively). Animals were evaluated by a laboratory veterinarian upon arrival at the laboratory,
Body and liver weights
Groups of rats ingesting approximately 75% of an ad libitum feed regimen (FR) had statistically identified lower body weights than either ad libitum fed groups (AL or PEF) from test day 2 to 3. Body weights of FR group animals were approximately 15–20% lower by the midpoint in the study (Figs. 1A and B). Administration of B(a)P had no effect upon the body weights for any group of rats. Similar results were obtained for nonfasted, terminal body weights (data not presented).
When averaged across
Discussion
The use of a multifactoral design and statistical evaluation employed in the present study provided a means of investigating the impact of multiple variables potentially encountered in the hazard evaluation of chemicals upon several xenobiotic metabolizing enzymes. Variations in genome expression patterns for the same experimental groups examined in the present study have been presented separately by Kan et al. (2003). As noted, constitutive activity data were examined statistically relative to
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Increased mitochondrial content and function by resveratrol and select flavonoids protects against benzo[a]pyrene-induced bioenergetic dysfunction and ROS generation in a cell model of neoplastic transformation
2020, Free Radical Biology and MedicineCitation Excerpt :Several possible mechanisms could account for the decrease in mitochondrial content by B[a]P. Previous studies have shown metabolites of B[a]P to alkylate mtDNA 40–90 times greater than nuclear DNA [5] and to deplete mtDNA [32]. And in addition to constitutive levels of B[a]P-activating enzymes [33,34], our previous observation [35] that exposure of Bhas 42 cells to B[a]P for 24 h strongly increased mRNA for inducible enzymes that activate B[a]P to mutagenic diol epoxide metabolites, supports that these metabolites would be produced in the cells. The exposure to B[a]P metabolites may produce adducts that interfere with mtDNA replication, or produce mutations that increase mitochondrial oxidative stress and decrease mitochondrial content through mitophagy [36].
Chapter 33 - Factors That Can Influence Animal Research
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