Toxicology Letters 195 (2010) 147–154
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Toxicology Letters
journal homepage: www.elsevier.com/locate/toxlet
The effect of -naphthoflavone on the metabolism of amiodarone by hepatic and
extra-hepatic microsomes
Marwa E. Elsherbiny, Ayman O.S. El-Kadi, Dion R. Brocks
∗
Faculty of Pharmacy and Pharmaceutical Sciences, University of Alberta, Edmonton, Alberta, Canada T6G 2N8
article info
Article history:
Received 3 February 2010
Received in revised form 18 March 2010
Accepted 24 March 2010
Available online 1 April 2010
Keywords:
Cytochrome P450
Amiodarone toxicity
Gene expression
CYP1A
Polycyclic aromatic hydrocarbons
Induction
abstract
Amiodarone is a potent antiarrhythmic drug with several limiting side effects, some of which have
been correlated with increased levels of its more toxic metabolite, desethylamiodarone. Elevated serum
desethylamiodarone to amiodarone ratios are associated with a risk of amiodarone-induced pulmonary
toxicity. Polycyclic aromatic hydrocarbons such as -naphthoflavone are known to increase desethy-
lamiodarone levels in rat in vivo. In this article we investigated if this increase was solely due to increased
formation as a result of cytochrome P450 (CYP) 1A1 and 1A2 induction in different rat hepatic and extra-
hepatic tissues. Additionally, the effect of amiodarone treatment on CYP1A1 and 1A2 gene expression and
activity was investigated. In rats, -naphthoflavone was found to increase desethylamiodarone forming
activity in lung and kidney microsomes. Amiodarone increased -naphthoflavone mediated induction of
CYP1A1 gene expression in liver, lung and kidney. However, there was no significant change in CYP1A
activity. As expected, the data indicated that the increase in desethylamiodarone levels in vivo was partly
due to increased formation through CYP1A1 induction, although increased formation was only evident
in some extra-hepatic tissues. Amiodarone treatment did not affect basal or induced CYP1A activity.
© 2010 Elsevier Ireland Ltd. All rights reserved.
1. Introduction
Amiodarone (AM) is a benzofuran derivative commonly pre-
scribed for the treatment of ventricular and supraventricular
arrhythmias (Naccarelli et al., 2000; Piccini et al., 2009; Snider
et al., 2009). It has a large volume of distribution, being exten-
sively sequestered by tissues such as lung, liver and adipose tissues
(Brien et al., 1987; Holt et al., 1983; Shayeganpour et al., 2008).
Metabolic transformation in the liver is the main route for AM elim-
ination (Fabre et al., 1993; Trivier et al., 1993). To date, there is
evidence of several metabolites being formed from AM biotrans-
formation (Ha et al., 2001; Young and Mehendale, 1986). The main
circulating metabolite, however, is mono-N-desethylamiodarone
(DEA), which is detectable at relatively high levels in serum and/or
plasma and tissues of human and preclinical animal species (Brien
et al., 1987; Elsherbiny and Brocks, 2010; Hamdy and Brocks, 2009;
Kannan et al., 1989; Meng et al., 2001; Shayeganpour et al., 2008;
Stark et al., 1991). Notably, DEA also possesses electrophysiolog-
ical activity similar to that of its parent drug (Stark et al., 1991).
Several cytochrome P450 (CYP) isoenzymes are involved in the bio-
∗
Corresponding author at: Faculty of Pharmacy and Pharmaceutical Sciences,
3118 Dentistry/Pharmacy Centre, University of Alberta, Edmonton, Alberta, Canada
T6G 2N8. Tel.: +1 780 492 2953; fax: +1 780 492 1217.
E-mail address: dbrocks@pharmacy.ualberta.ca (D.R. Brocks).
transformation of AM to DEA. For example, CYP3A4, 1A1/2, 2D6
and 2C8 were found to be involved in DEA formation in human
whereas CYP3A1/2, 1A1, 2C11 and 2D1 were found to mediate DEA
formation in rat (Elsherbiny et al., 2008; Ohyama et al., 2000a;
Shayeganpour et al., 2006).
Despite the beneficial use of AM in the treatment of arrhyth-
mias, AM use is sometimes discontinued because of some serious
side effects. These adverse effects can involve liver, thyroid, skin,
pancreas and lung (Batcher et al., 2007; Chen et al., 2007; Jarand et
al., 2007; Puli et al., 2005). In several organs, DEA has been shown to
be more toxic than AM. For example, DEA caused a decrease in the
mitochondrial membrane potential and cell death in human and
rat pulmonary alveolar epithelial cells at lower concentrations than
those of AM (Bargout et al., 2000; Bolt et al., 2001). The concentra-
tions in human alveolar epithelial cell lines (A549) that resulted in
50% cell death were recently reported to be 50 and 12 M for AM
and DEA, respectively (Seki et al., 2008). Furthermore, this more
potent cytotoxic effect of DEA was consistently observed in human
hepatocellular carcinoma (HepG2) and immortalized thyrocytes
cell line (SGHTL-34 cells) (Beddows et al., 1989; Waldhauser et
al., 2006) with similar observations being documented in animal
models such as the rat (Somani et al., 1990).
Exposure to polycyclic aromatic hydrocarbons (PAH), potent
CYP1A inducers, can lead to significant increases in the DEA lev-
els in the plasma, liver, heart and lung tissues of AM treated rats
(Elsherbiny and Brocks, 2010). Although these compounds are con-
0378-4274/$ – see front matter © 2010 Elsevier Ireland Ltd. All rights reserved.
doi:10.1016/j.toxlet.2010.03.019