1Department of Pharmaceutical Sciences, Babasaheb Bhimrao Ambedkar University, Vidya Vihar, Rai Bareli Road, Lucknow 226025, India, 2Department of Pharmaceutical Technology, Jadavpur University, Kolkata 700032, India, 3Department of Pharmaceutical Sciences, Joyti Vidyapeeth Women’s University, Jaipur, Rajasthan
Email: sudiptapharm@gmail.com
Received: 04 Sep 2015 Revised and Accepted: 09 Sep 2016
ABSTRACT
Objective: Duloxetine, a selective serotonin and noradrenaline reuptake inhibitor used in major depressive disorders, urinary incontinence and diabetic peripheral neuropathic pain. It is reported to be associated with several types of liver injuries, including hepatocellular, cholestatic and mixed hepatocellular-cholestatic patterns. The objective of this study was to assess the effect of duloxetine or its metabolites on oxidative stress-induced liver damages.
Methods: In this study, animals were divided into five groups. In the first group, the only vehicle was given orally for 21 d. The second group has been considered as hepatotoxic control group where Erythromycin was given orally for 14 d and remaining three groups have been considered as test groups where duloxetine, fluvoxamine and duloxetine along with fluvoxamine were administered orally for 21 d. Liver GSH, oxidised lipid malonaldehyde (MDA), superoxide dismutase (SOD), catalase (CAT), protein carbonyl (PC) and plasma alanine transaminase (ALT), aspartate transaminase (AST) and alkaline phosphatase (ALP) levels were measured to determine the level of hepatotoxicity. Scanning electron microscopy (SEM) study of liver tissues was also performed to examine the liver injuries.
Results: GSH and SOD levels were found to be decreased in duloxetine-treated groups with respect to the hepatotoxic control group, whereas increased level of MDA, CAT and PC signify the damages of liver cells. Increased level of plasma ALT, AST and ALP at the same time indicated liver tissue damage. Opposite effects were observed in the case of duloxetine and fluvoxamine-treated groups. SEM of liver tissues revealed that the tissue injury occurred in Duloxetin treated groups, whereas the restoration of normal tissue architecture took place due to the administration of duloxetine and fluvoxamine-treated groups.
Conclusion: Our results collectively indicated that hydroxylated and epoxide metabolites of duloxetine might have hepatotoxic potential due to oxidative stress produced by the release of free radicals or reactive oxygen species.
Keywords: Duloxetine, CYP1A2 enzyme, Hepatotoxicity, Oxidative stress
© 2016 The Authors. Published by Innovare Academic Sciences Pvt Ltd. This is an open access article under the CC BY license (http://creativecommons. org/licenses/by/4. 0/)
DOI: http://dx.doi.org/10.22159/ijpps.2016v8i11.8857
INTRODUCTION
Duloxetine (DLX, fig. 1A) [N-methyl-γ-(1-naphthyloxy)-2-thiophene-propylamine] is a selective serotonin and noradrenaline reuptake inhibitor, approved by the USFDA for the treatment of major depressive disorders. In addition, it is also used in stress-induced urinary incontinence and diabetic peripheral neuropathic pain [1]. DLX is highly bind to plasma proteins (>90%) and mainly metabolised by various cytochrome (CYP) enzymes, such as CYP1A2 and CYP2D6 in humans. Although, the naphthyl ring underwent epoxidation and subsequently formed adduct with glutathione (GSH), but thiophene moiety showed inert after bioactivation [1]. The bioactivation of naphthyl ring mediated through CYP1A2 enzyme corresponds to 4-hydroxy DLX, 6-hydroxy-5-methoxy DLX and 4, 6-dihydroxy DLX [4]. Sometimes, naphthyl ring could generate reactive metabolites, i.e. epoxides which may cause hepatotoxicity [2]. The role of the CYP2D6 enzyme during bioactivation of DLX was not prominent in the case of both rats and humans.
Fig. 1: Structures of (A) DLX and (B) FLX
Recently, it has been reported that DLX was reported to be associated with several cases of hepatocellular, cholestatic and mixed hepatocellular-cholestatic patterns of liver injuries [3]. Hepatobiliary diseases were estimated to occur in about 8 per 100,000 cases, while elevation of enzyme level increased thrice the value of normal range as observed in 0.9 to 1.7% of DLX treated subjects [4, 5]. Idiosyncratic liver damages were estimated to occur about 1-2 per 100,000 cases of exposure in DLX [4]. In a pooled analysis of 17615 subjects, the incidence of serum ALT level was increased three times than normal value [6]. Hanje et al. (2006) reported and explained the cause of fulminant hepatic failure and death during DLX therapy [7]. Taking into all these considerations related to DLX inducing hepatotoxicity, the question arose whether DLX or its metabolites has any role in hepatotoxicity or not? It has been reported that DLX is metabolised by both CYP1A2 and CYP2D6. Therefore, the objective of this study was to evaluate the effect of Duloxetine or its metabolites on oxidative stress-induced hepatotoxicity. In order to further ascertain the oxidative stress-induced hepatotoxicity, docking studies were also performed accordingly.
MATERIALS AND METHODS
Materials
Duloxetine (DLX; Batch Number: DL0040713) and Fluvoxamine (FLX; fig. 1B, Batch Number: LT-OFLM/014/12-13) were received from Indian companies namely Hetero Drugs Limited, Hyderabad, and Mehta API Pvt Ltd, Mumbai, respectively. Disodium ethylenediamine tetraacetic acid (EDTA), disodium hydrogen phosphate, potassium dihydrogen phosphate, sodium citrate and trichloroacetic acid were purchased from SD Fine Chemicals, Mumbai, India. 5, 5´-dithiotris-2-nitro benzoic acid, tris buffer, sodium carbonate, glacial metaphosphoric acid, sodium potassium tartrate and sodium chloride were purchased from Loba Chemicals, New Delhi, India. Erythromycin stearate (ERY) was obtained from Himedia, Mumbai, India. All the solvents, reagents and chemicals were of analytical grades with 99% purity and in-house distilled water was used throughout the experiment.
Docking studies
Docking studies of DLX were performed using Argus lab, Pyrx virtual screening 0.8 and Autodock 4.0 along with Autodock vina. Before the docking study, we identified the active site domain using DogP active site recognize where the ligand has been shown the best configuration. Later, grid box was set according to previously recognised active site amino acid sequence. Finally, their binding affinity (kcal/mol) and counting of probable hydrogen bonds were evaluated.
Animal grouping and experimental design
Male Wistar rats (weighing 90-140 g) were purchased from Animal House, CSIR-CDRI, Lucknow, India (Approval No. UIP/IAEC/ 2014/FEB./07) and were kept in polypropylene cages under standard conditions of temperature (25±1 °C) with 12 h light and dark conditions, diet and water ad libitum for 7 d. Animals were randomised and divided into following 5 groups having 6 animals in each group (n=6). Rats were kept fasted overnight before starting the experiment with free excess to water. Drugs were dissolved separately in distilled water as per the following treatment schedule. The first group served as normal control where animals were given only vehicle orally (1 ml/kg BW) for 21 d.
The second group has been considered as hepatotoxic control, where ERY was given orally (100 mg/kg BW, served as hepatotoxicity control) for 14 d [8]. The remaining three groups have been considered as test groups where DLX, FLX and DLX+FLX were administered orally in doses of 10, 30 and 10+30 mg/kg body weight, respectively for 21 d [9, 10]. On 14th (for the hepatotoxic control group) and 21st days, blood samples were collected from retro-orbital plexus and centrifuged to separate plasma and kept at ‒20 °C for further biochemical estimations. Rats from each group were sacrificed by cervical dislocation; livers were removed and kept in ‒20 °C for further biochemical estimation.
Estimation of plasma ALT, AST and ALP
Plasma ALT, AST [11] and ALP [12] were estimated according to the method as described earlier with slight modifications using specific assay kits obtained from Excel Diagnostics Pvt. Ltd., Hyderabad, India.
Estimation of Tissue GSH, CAT, MDA, SOD, and PC
Tissue GSH [13], CAT [14], MDA and SOD [15], and PC [16] levels were estimated as per the method reported earlier with or without slight modifications.
Scanning electron microscopic (SEM) study of liver tissue
Rat liver samples were mixed with 2.5% (v/v) of glutaraldehyde and were kept at 4 °C for 2-6 h. Then, the samples were washed with 0.1 (M) phosphate buffer 3 times for 15 min interval. After that, 1% (w/v) osmium tetroxide was added to it and kept for 2 h at 4 °C and the samples were washed with 0.1 (M) phosphate buffer 3 times for 15 min interval. Later, the specimens were dehydrated by using an increase in the percentage of drying (30%, 50%, 70%, 90%, 95%, and 100% v/v) to remove excess water from the samples at 4 °C for about 30 min period. After that, all specimens were dried in air and the critical point of drying was maintained at 31.5 °C and pressure at 1100 psi. Finally, the samples were mounted onto the aluminium stubs with adhesive tape and observed the images using scanning electron microscope (JSM-6490LV. Jeol, Japan).
Statistical analysis
Statistical analysis was carried out using GraphPad Prism 5.0 (Graph Pad Software, San Diago, CA). All results were expressed as mean±Standard deviation (SD). The data were analysed by one-way ANOVA (analysis of variances) followed by Bonferroni multiple comparison tests. For biochemical estimations, statistical significance differences were considered with respect to control group (aP<0.05, bP<0.01, cP<0.001).
RESULTS
Docking studies
Docking images of DLX along with two target enzymes has been shown in fig. 2. DLX exhibited good binding affinity with CYP1A2 enzyme (value-10.2 kcal/mol and one H-bond) whereas lower binding affinity was observed in the case of CYP2D6 (value-7.5 kcal/mol and no H-bond) (table 1).
Table 1: Binding affinities of DLX with human CYP1A2 AND CYP2D6. Comparatively, studies were performed by using various commercially available virtual Dockers
Receptor | Affinity (kcal/mol) Auto dock |
Affinity (kcal/mol) Argus lab |
Affinity (kcal/mol) Pyrx 8.0 |
Amino acids involved in interactions |
H-bonds |
Cytochrome 450 1A2 | -10.2 | -14.97 | -9.7 | ILE430, ALA484, LEU463, GLY460, GLY318, ILE314, ASP313, LEU144 |
1 |
Cytochrome 450 2D6 | -7.5 | -11.80 | -8.1 | THR349, LYS345, GLU348, THR367, PRO366, THR438, GLY437 | 0 |
Fig. 2: Docking images of (A) DLX with human CYP1A2 (2HI4) and (B) DLX with human CYP2D6 (2F9Q). The round mesh circular showed the binding affinity of ligand with amino acids involved in binding poses
Plasma ALT, AST and ALP
ALT level was slightly higher in DLX (~ 57 U/ml) treated group than normal control group (~ 40 U/ml) as shown in table 2. ALT (~ 37 and 32 U/ml) level in plasma was found to be decreased in both FLX and DLX+FLX treated groups. ERY acted as a hepatotoxic control, which demonstrated the higher concentration of ALT in plasma. There was a significant increase in plasma AST level in both ERY (~182 U/ml) and DLX treated groups (~174 U/ml). AST level (~150 U/ml) was closer to normal control after FLX and DLX+FLX treated groups. A similar result of plasma concentration of ALP was higher in both ERY and DLX treated groups. FLX and DLX+FLX treated groups also showed the similar higher concentration of plasma ALP in compared to normal control (table 2).
Table 2: Various enzyme concentrations in plasma
Groups | ALT (U/ml) | AST (U/ml) | ALP (U/ml) |
Control | 40.10±2.71 | 150.00±7.62 | 830.53±8.98 |
ERY | 56.37±1.42 | 182.37±8.01 | 956.93±4.55 |
DLX | 57.23±2.39a | 174.2±7.82a | 914.67±6.88b |
FLX | 37.5±1.98 | 143.5±7.95 | 820.33±9.53 |
DLX+FLX | 32.6±2.82a | 147.83±8.06 | 780.95±1.18 |
Data were presented as mean±SD (n=6). Statistically, significant differences were observed between control and test groups [one way-ANOVA followed by Bonferroni multiple comparison test; (a𝑃<0.001, b𝑃<0.01)]
Biochemical estimations in liver tissues
In order to understand the mechanism of hepatotoxicity of DLX in Wistar rats, various oxidative stress-related parameters like GSH, MDA, SOD, CAT and PC in liver tissues were measured. As depicted in table 3, it was observed that GSH level was found to be decreased in DLX treated group. DLX and DLX+FLX treated groups also showed no toxic effect because of similar concentrations of biochemical parameters as in normal control. The level of MDA was higher in both ERY and DLX treated groups (~ 2.0 nM/mg of protein) as shown in table 3. This concentration again normalised for FLX and DLX+FLX treated groups. Similar trends were also observed for PC assay where the formation of PC was higher in ERY and DLX treated groups (table 3). In order to determine the oxidative stress-based hepatotoxicity, CAT and SOD enzyme level was measured separately. CAT is most abundant in the liver, which is mainly responsible for the catalytic decomposition of H2O2. Increase in concentration of H2O2 in DLX treated group depicted that there was less amount of CAT enzyme available in the tissues to decompose H2O2 (table 3). It was observed that SOD enzyme level was also decreased in DLX treated group in compared to normal control, FLX and DLX+FLX treated groups.
Table 3: Various oxidative stress parameters in liver
Groups | SOD (U/mg of Protein) | CAT (nM H2O2 decomposed/min/mg of protein ) | GSH (µM/mg of Protein) | TBARS (nM of MDA/mg of protein) |
PC (µg/mg of protein) |
Control | 2.23±0.13 | 75.20±4.51 | 60.67±3.64 | 1.79±0.29 | 0.41±0.03 |
ERY | 1.11±0.06 | 58.33±5.50 | 42.15±2.52 | 5.36±0.22 | 0.69±0.04 |
DLX | 1.17±0.07a | 97.88±5.87a | 37.80±2.96a | 5.12±0.20a | 0.65±0.05a |
FLX | 2.17±0.18 | 70.87±5.39 | 63.01±2.68 | 1.41±0.20 | 0.41±0.03 |
DLX+FLX | 1.80±0.10a | 34.24±4.05a | 60.46±4.82 | 2.43±0.14a | 0.42±0.02 |
Data represented as mean±SD (n=6). Statistically, significant differences were observed between control and test groups [one way-ANOVA followed by Bonferroni multiple comparison test; ap<0.001]
SEM analysis of liver
SEM analysis showed the presence of lesions in DLX treated group, whereas, it was absent in both FLX and DLX+FLX treated groups (fig. 3).
Fig. 3: SWM photomicrographs of the liver tissues (A) Control, (B) ERY, (C) DLX, (D) FLX and (E) DLX+FLX. Tissue necrosis was observed in ERY and DLX treated rats which were less prominent in both FLX and DLX+FLX treated rats
DISCUSSION
Most of the hepatotoxic drugs are generally involved in increasing levels of liver enzymes and GSH level due to oxidative stress induced by some specific drugs, whereas some other drugs may take part in the alteration of liver mitochondrial functions and expression of liver genes [17-19]. Mechanism of oxidative stress also plays an important role in causing hepatotoxicity produced by some drugs like acetaminophen [20]. It is assumed that some orally administered drugs are involved in the generation of free radicals which may further elevate the tissue TBARS, PC and may reduce the CAT, GSH and SOD levels in liver, and increased level of plasma ALT, AST and ALP were collectively responsible for liver damages.
Orally active DLX was metabolised by CYP1A2 to corresponding hydroxylated and epoxide metabolites which had a tendency to bind with GSH [1, 2]. This practical data was also confirmed by docking studies where we found that CYP1A2 was the major enzyme for DLX metabolism (fig. 2 and table 1). Taking into consideration of above observations, it was questionable whether parent DLX is hepatotoxic or its metabolites. To get the actual answer, metabolism of DLX using FLX (CYP1A2 inhibitor) was conducted, and various biochemical parameters were evaluated.
Our results collectively suggested that all the enzyme levels were higher for DLX treated groups than control group whereas this level is slightly lower for both FLX and DLX+FLX treated groups as shown in table 2. Both AST and ALT are the liver enzymes which is responsible for transamination of amino acids, whereas ALP is responsible for catalysis of organic phosphate esters. These are the key enzymes of liver, which are extracted out during liver damages [16, 21]. The increase of these enzymes in plasma during DLX treatment indicated the hepatic damage, which was further improved by FLX treatment. This was an indirect indication of liver damage, but it could not be explained how DLX produced toxicity in the liver after oral administration.
The DLX treated rats depleted more reduced glutathione (GSH) than FLX and DLX+FLX treated groups (table 3). GSH is a tripeptide, which is most abundant in all tissues including liver. GSH has a major role in oxidation-reduction process, resulting in the formation of disulfide glutathione (GSSG) [22] during oxidative damage. Reduction of GSH level by DLX is an indication of oxidative stress-induced liver damage, which was improved during FLX treatment. The decrease in the levels of GSH in DLX treated rats represented the higher utilisation of GSH during oxidative damage which was completely restored during a single dose of FLX and combined dose of FLX with DLX.
To prove the oxidative stress induced hepatotoxicity, the tissue MDA levels were also performed. Oxidation of lipids is another important parameter to measure the oxidative stress in living body [17]. From the result; it was observed that tissue MDA level was higher for DLX treated group, which was again restored to a normal level during FLX, and DLX+FLX treated rats (table 3). The Higher amount of MDA formation during DLX treatment was directly represented the oxidative damage of liver cells. Thus, the results indicated that DLX might be responsible for hepatotoxicity due to oxidative damages.
In order to understand the relationship between oxidative stress and hepatotoxicity, PC assay was performed where a higher amount of PC was formed than DLX treated groups (table 3). The carboxyl group of protein become oxidised due to the formation of reactive oxygen species [23] and converted to PC, which is an important marker for oxidative stress. As depicted in table 3, DLX treated groups formed more PC than FLX and DLX+FLX treated groups which were an important indication of oxidative stress-induced liver damages.
In order to further understand the mechanism of oxidative stress, both CAT and SOD enzyme levels in liver were measured. The enzyme CAT is also most abundant in the liver which catalyses the conversion of H2O2 to corresponding oxygen and water. The action of this enzyme is reduced due to the presence of peroxides and reactive oxygen species [24, 25]. H2O2 levels were measured, and values were compared between various treated groups. Increase in concentration of H2O2 in DLX treated sample depicted that there were less amount of CAT enzyme available in the tissue to decompose the H2O2 with respect to control and other treated groups (table 3). This assay indirectly indicated that oral administration of DLX reduced the level of CAT enzyme in the liver. Separately, the estimation of SOD levels in liver was performed. The SOD levels were also decreased in DLX treated groups, but the level of this enzyme became normal in FLX and DLX+FLX treated rats (table 3).
For direct evidence of liver damages, SEM analyses of liver tissues were performed (fig. 3) and damages of liver tissues were observed in DLX treated rats which were absent in FLX, and DLX+FLX treated groups.
CONCLUSION
The hepatotoxicity of DLX might be due to oxidative stress produced by hydroxylated and epoxide metabolites, which may release free radicals or reactive oxygen species. Further studies in this context, such as preparation of hydroxylated and epoxide metabolites and measurement of their hepatotoxic potential are beyond the scope of this study.
ACKNOWLEDGEMENT
Dr. Sudipta Saha (Corresponding Author) would like to thank the University Grants Commission (UGC), New Delhi, India, for providing UGC Start-Up-Grant [Grant No. F. 20-1/2012 (BSR)/20-7 (15)/2012 (BSR)].
CONFLICT OF INTERESTS
Authors declare that they have no conflict of interest.
REFERENCES
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