Assessment of fipronil toxicity on wistar rats: A hepatotoxic perspective.

Extensive pesticide application has contributed to environmental contamination globally, imposing adverse health effects on non-target organisms. Need for an understanding of cellular response following pesticide exposure is, therefore, paradigmatic for elucidating perturbations occurring within biological systems. The present investigation was aimed to examine safe and toxic dose level of a persistent, synthetic, phenylpyrazole based insecticide, Fipronil (FPN) on rat liver. Experimental animals were divided into four groups and gavaged with 0.0 (control), 32.33 (high), 12.12 (medium) and 6.46 mg/kg body weight/day (low dose) of FPN for 90 days. While results for liver catalase and glutathione S-transferase indicated significant changes in high and medium dose groups, the superoxide dismutase and glutathione peroxidase activity suggested significant changes in all exposed groups as compared to control. Elevated levels of liver malondialdehyde reflected oxidative damage potential under the exposed groups but remained insignificant for low dose. Histologically, structural irregularities with findings like impaired portal vein and hypertrophy of hepatocytes were prominent under all the exposed groups. The FT-IR based spectral investigation further revealed changes in absorption patterns and peak intensities in rats exposed to FPN. Significant elevation was also noticed in liver enzymes; alanine aminotransferase, aspartate aminotransferase and alkaline phosphatase in rat serum suggesting the toxicity in dose -dependent pattern. Based on the outcome, it could be ascertained that the toxicity of FPN is certain at high and medium dose levels but remains ambiguous at a low dose of 6.46 mg/kg body weight/day. The current upshots serve as a preliminary report thereby advising the farming community against the usage of FPN insecticide.

Introduction

Large -scale anthropogenic activities under chemical scale have predominantly contributed to environmental contamination globally [1]. Increased chemical persistence, mainly pesticides, in soil and water have found their direct correlation to deteriorating health conditions of non-target species ranging from amphibians to mammals [[2], [3]]. Pesticides belong to the only group of chemical toxicants that are intentionally applied to the environment with an objective of enhancing food production through countering insect pests and controlling disease vectors additionally [4]. Even though the consequences of pesticide toxicity are known to be many, establishment of oxidative stress is high paradigm due to the occurrence of reactive oxygen species (ROS) in all aerobic individuals [5]. Upshots in the imbalance of oxidant and antioxidant magnitudes, basically due to elevated proportions of ROS in vivo is therefore considered as an imperative indicator of chemical stress [6]. ROS, as known, is an inevitable and obligatory composite of aerobic mechanism, often produced paradoxically in hepatocytic mitochondria and endoplasmic reticulum, channelized through cytochrome P450 cluster [7]. Although its role in signaling pathways is highly critical, its existence in surplus amounts could impart catastrophic damage to cellular proteins, with the processes often being irreversible [8].

Besides, the mammalian liver is of exceptional concern for studying pesticide -induced toxicity in various experimental models [9]. Its ability to carry out detoxification contributes to homeostasis [10]. Hepatocytic proteins, lipids, and DNA on other hand are among the cellular structures that are primarily affected by ROS that basically arises through exposure to toxic chemicals [11]. The process has been found to result in structural and functional discrepancies of hepatic tissue, ultimately resulting in the impaired health. Attrition of liver as a consequence of incessant detoxification is often reflected by an upsurge in liver enzymes [12]. Basic tools for determining the damage to the liver include the assay of liver enzymes; alanine aminotransferase (ALT), aspartate aminotransferase (AST), and alkaline phosphatase (ALP) levels from blood serum. These components and the end products of the metabolic pathways are highly sensitive for determining the incurred abnormality and have been considered as biochemical markers of liver dysfunction [13].

Fipronil (5- amino- 1- (2, 6-dichloro- α, α, α- trifluoro- p- tolyl)- 4-trifluoromethylsulfinylpyrazole-3- carbonitrile) a broad spectrum, first N- phenylpyrazole insecticide was introduced with an objective of controlling insect pest [14]. It has been found to be effective even against those pests which have gained resistance to the conventional insecticides [15]. The mechanism of FPN toxicity is presumed to be due to the inhibition of a neurotransmitter, a GABAA-gated chloride channel, rendering the organism to suffer from insufficient neurological threshold finally resulting in death [14]. Earlier reports have suggested the involvement of FPN in impeding the metabolic enzymatic systems that are often known to contain sulfhydryl groups and uncoupling of oxidative phosphorylation in the mitochondrial complex [16]. The process is often thought to result in increased lipid peroxidation, DNA damage, depletion of sulfhydryls, altered calcium homeostasis, hepatic congestion, ischemia, hypoxia and death [17].

FT-IR (Fourier Transformed Infra-Red) based spectroscopy analysis has been considered as one of the important tools under vibrational spectroscopic technique, widely used for detection and quantification of macromolecules in biological samples [[18], [19], [20]]. Increase in the levels of serum AST, ALT and ALP reflects the loss of biochemical and structural integrity of the liver and is the most preferred diagnostic tool to evaluate hepatocellular injury [12]. Even though FPN is known to generate oxidative stress and cause the histopathological alterations in hepatic tissue [21], its lipophilic nature and the mechanism underlining its metabolic fate and disposition through mechanisms involved in mammal liver have been poorly understood. Therefore, an attempt has been made in the current study to investigate the FPN induced hepatotoxicity by evaluating biochemical, histopathological and biophysical means following subchronic exposure tenures.

Materials and methods

Animal procurement

Male Wistar albino rats (8 weeks) were obtained from animal house facility, Department of PG studies and Research in Zoology, Karnatak University, Dharwad, Karnataka, India. Rats were housed in the polypropylene cages with ad libitum access to standard pellet feed and drinking water. The room was maintained under a 12/12 h light– dark cycle, an ambient temperature of 23–30 °C with a relative humidity of 45.0 (±15)%.

Experimental design and test doses

For a 90 day study of oral toxicity, the 6–7 week old Wistar rats were randomly assigned into four groups of six males each. While first group of rats served as the control, the other three group received 32.33 (high), 12.12 (medium) and 6.46 mg/kg body weight/day (low dose) of FPN dose respectively in drinking water. On completion of the exposure duration, the rats were euthanized by carbon dioxide inhalation followed by cervical dislocation. The necessary tissue/organs were isolated.

Antioxidant enzyme assay

Catalase activity

The Catalase (CAT; EC 1.11.1.6) activity was determined by measuring the decrease of hydrogen peroxide concentration at 240 nm according to Luck [22]. The reaction mixture consisted of 50 mM potassium phosphate buffer (pH 7.0) and 10 mM H2O2 freshly added. The enzyme activity was expressed as U/mg protein.

Superoxide dismutase activity

Superoxide dismutase (SOD; EC 1.15.1.1) activity was measured by methodology as described by Kakkar et al., [23]. The reaction mixture consisted of 0.052 M sodium pyrophosphate buffer (pH 8.4), 186 μM phenazine methosulphate (PMS), 30 μM nitroblue tetrazolium chloride (NBT) and 780 μM NADH. Activity is reported in units of SOD per milligram of protein. The activity was calculated wherein, one unit of the enzyme concentration required to inhibit 50% of the optical density of chromagen formed in one unit at 560 nm under the assay condition. The values were expressed in terms of U/mg protein.

Glutathione peroxidase activity

Glutathione peroxidase (GPx; EC 1.11.1.9) activity was measured by the method of Paglia and Valentine [24]. The (GSSG) generated by GPx was reduced by GR, and NADPH oxidation was monitored at 340 nm using Spectrophotometer. The reaction mixture consisted of 50 mM potassium phosphate buffer (pH 7), 1 mM EDTA, 0.1 E.U/mL oxidised glutathione reductase (GSSG), 1 mM sodium azide, 1 mM reduced glutathione (GSG), 0.2 mM NADPH, and 25 mM H2O2. The enzyme activity was expressed as mU/mg protein. Wherein one mU is the amount that catalyses 1 nmoles of NADPH per minute.

Glutathione S-transferase activity

Glutathione S-transferase (GST; EC 2.5.1.18) activity was assayed by the method of Habig et al. [25]. The increase in absorbance was noted at 340 nm using 1-chloro-2,4-dinitrobenzene (CDNB). The reaction mixture 0.3 mM phosphate buffer (pH 6.5), 30 mM 1-chloro-2, 4-dinitrobenzene (CDNB) and double distilled water. After pre incubating the reaction mixture at 37 °C for 5 min, the reaction was started by the addition of homogenate and glutathione as substrate. The absorbance was followed for 5 min at 340 nm. The enzyme activity was calculated as U/mg protein.

Lipid peroxidation

Lipid peroxidation (LPO) level was performed according to the method of Buege and Aust [26] and estimated by thiobarbituric acid reactive substance (TBARS) assay performed by an optically measured malondialdehyde (MDA) reaction with TBA. To the liver homogenate, 10% trichloroacetic and 0.67% thiobarbituric acid were added to adjust to a final volume of 1.0 ml. The reaction mixture was placed in a microcentrifuge tube and incubated for 15 min at 95 °C. After cooling, it was centrifuged at 5000×g for 15 min, and optical density was measured by a spectrophotometer at 530 nm. TBARS levels were expressed as nmol MDA/mg protein.

Histopathology

For the histopathological examination, the method was followed as described by Humason [27]. The liver was isolated and immediately fixed in Bouin’s fluid for 24–48 h. The tissue was processed in a series of graded alcohol and embedded in paraffin which was being filtered thrice earlier. The organs embedded in paraffin were sectioned into 5 μm-thick ribbons by using semi-automated microtome (LeicaRM 2255), and sections were stained primarily with haematoxylin and counterstained with eosin (H&E) for light microscopic examination [28]. The sections were observed under ×200 magnification. The microscopic view was photographed by using an Olympus phase-contrast microscope (Olympus BX51, Tokyo, Japan) with attached photography machinery (ProgResC3, Jenoptic- Germany). The photographed images were further observed for differences, and the findings were recorded. The photomicrograph was processed with Adobe Photoshop 7.0 for slight management in brightness and contrast. The captured images were processed with ImageJ (V. 1.50i) software for enhanced understanding of structural changes.

FT-IR spectroscopy

The liver was gently washed with phosphate buffered saline, blot dried and immediately immersed in liquid nitrogen and crushed in a mortar and pestle to obtain homogenate. This was further lyophilized prior to infrared analysis. For the infrared measurement, KBr/sample disks were prepared (0.1998 g of powdered KBr with 0.0002 g sample) to reach a total of 0.2 g of KBr/sample mixture and were measured IR spectrophotometrically according to Paul and Robert [29]. The IR for each sample was measured in triplicate using a Shimadzu FTIR–8400 s spectrophotometer with a continuous nitrogen purge. The IR spectra recorded from different KBr disks represented only one spectrum for each experimental group after being co-added. Twenty scans were signal-averaged for a single spectrum with 4 cm−1 spectral resolution in the spectral range of 3600–500 cm−1, obtained at room temperature. IR spectra recorded from each group were co-added, and the entire spectra were normalized and baseline corrected, then subjected to the Kubelka-Munk algorithm [30] by the means of IR solution software [31].

Serum biochemistry

The blood samples were obtained from the experimental rats by cardiac puncture and were transferred to anticoagulant/heparin free tubes. The serum was separated by centrifugation. The separated serum was subjected to the method of Reitman and Frankel [32] to determine the levels of serum ALT and AST. The method of MacComb and Bowers [33] was carried out to determine the level of serum ALP.

Statistical analysis

The antioxidant activities are reported as the mean ± standard error of the mean (SEM) obtained from triplicates. The data were subjected to one-way analysis of variance and further subjected to Tukey’s test for post hoc analysis by defining the significance level at *p < 0.05, **p < 0.01.

Ethics statement

The present study was carried out at the Department of PG Studies and Research in Zoology, Karnatak University, Dharwad (Karnataka, India) as per the ethics committee regulations. The test animals used were maintained and subjected to experimentation process as well as disposed upon completion of the experiment as per the guidelines issued by CPCSEA (Committee for the Purpose of Control and Supervision of Experiments on Animals) (Animal House Registration No. 639/02/a/CPCSEA) guidelines were followed for maintenance, use and disposal of the experimental animals. All the experiments were conducted in accordance with IAEC (Institutional Animal Ethics Committee).

Results and discussion

Toxicity signs

No mortality was recorded in rats under control or exposed groups. Additionally, no severe clinical signs or symptoms were noticed in rats exposed to sublethal doses of FPN or under control.

Body weight gain

The changes in body weight gain under control rats and those exposed to different sublethal doses of FPN are given in Fig. 1.

Fig. 1

Changes in body weight gain of male rats under control and exposed group.

Significant variation in enzymatic activity of antioxidant enzymes was noticed in the liver of rats exposed to high and medium dose FPN unlike in rats under low dose group when compared to control (Table 1). Percent decline of −54.37% was noticed for CAT in rats administered with a high dose of FPN, this was followed by −21.19% in rats intoxicated with medium dose. A mild elevation (6.25%) in CAT was noticed in the liver of rats dosed with low FPN which, however, remained insignificant with respect to control group. The SOD activity under FPN stress also reduced significantly with percent decline of −54.49 and −48.43% under high and medium dose respectively. However, the rats under low dose demonstrated a significant elevation in SOD which was recorded to be 24.89%. The existence of SOD–CAT combined system is known to act as the first line of defence against ROS induced damage, thus these activities are used as biomarkers to indicate the exorbitant production of ROS [34]. The current outcome is consistent with studies of Sayeed et al. [35]; Crestani et al., [36] and Kartheek and David [37] who reported a decrease in CAT and SOD magnitudes in the liver following exposure to deltamethrin, clomazone, and sodium cyanide respectively. The present condition characterized by the metabolism of FPN on regular intervals could have led to the production of free radicals that might have chemically modified essential biomolecules specifically proteins and lipids resulting in the condition of LPO [38].

Table 1

Changes in antioxidant status of wistar rats on exposure to selected doses of fipronil.

Sl. No.	Parameter	Groups
		Control	Exposed
			High	Medium	Low
1.	Catalase (U/mg protein)	13.26 ± 0.19	6.05 ± 0.43**	10.45 ± 0.87*	14.09 ± 0.52
2.	Superoxide dismutase (U/mg protein)	48.37 ± 0.27	22.01 ± 0.8**	24.94 ± 0.66**	60.41 ± 0.72*
3.	Glutathione peroxidase (U/mg protein)	190.07 ± 1.14	51.77 ± 0.93**	124.94 ± 0.44*	156.41 ± 0.91*
4.	Glutathione S-transferase (U/mg protein)	45.11 ± 0.71	19.77 ± 0.29**	24.51 ± 0.53*	42.64 ± 0.66
5.	Malondialdehyde (nmol of MDA formed/mg protein)	2.01 ± 0.08	7.33 ± 0.44**	4.15 ± 0.13*	2.59 ± 0.22*

Values represented in groups are means ± SE; significantly different from control.

p < 0.05.

p < 0.01.

Evaluation of GPx in the liver of exposed rats suggested a contrasting trend in its activity wherein the decline of −51.71, −34.26 and −17.70% was recorded for high, medium and low dose respectively. The possibilities for observing this trend may be due to the fact that GPx is oxidised completely if hydroperoxide and GSH concentrations are similar. The significant loss of GST activity in a similar pattern was witnessed, while the maximum decline (−56.17%) was recorded against high dose, a negligible change of −5.47% was noticed recorded for low dose group. The same, when recorded for medium dose revealed decline with a percent change of −45.66%. This decline could be as a consequence of depleted levels of cellular thiol which has been recognized as a crucial component of GST. A number of toxicants have been known to deplete the thiol content [[39], [40]]. Nonetheless, the mechanism by which the decline occurs remains unknown.

MDA is a major end product of LPO and is often thought to propagate and amplify oxidative injury [41]. Its evaluation helps in validating the intensity of damage to biological membranes [37]. In the present study, a significant elevation in LPO level was observed in exposure groups as compared with control group. While rats exposed to high dose of FPN indicated the highest MDA level which was found to be 284.57% as compared to control. While medium dose imparted a percent change of 106.46%, the low dose administration resulted in MDA elevation by 28.85%. A likely explanation for this could be that a much stronger oxidant than superoxide anion-radical could initiate the chain oxidation of polyunsaturated phospholipids, thus leading to impairment of membrane function [42]. The observed findings are in agreement with previously reported studies by Mossa et al., [21] wherein significant decline in antioxidant enzymes and elevation in MDA levels was observed in rats administered with sublethal FPN dose following 45 days of exposure.

Histological analysis

The histopathological findings in the liver of rats under control and exposed group is given in Table 2; Fig. 2, Fig. 3. Changes in histoarchitecture of liver was evidenced with findings like dilation of blood sinusoids (BS), ruptured/partial clogging of bile duct (BD) and portal vein (PV), damaged hepatic artery (HA) and connective tissue (CT), hypertrophy of hepatocytes (H), stagnation of bile (B), mild vacuolation (V) and focal necrosis (F). Nevertheless, no changes were recorded for the control group. Hepatic portal was found to exist intact with hepatic sinusoids indicating normal liver histoarchitecture. Similar reports have been presented previously in different animal models by various authors [11]. The previous reports indicate that defenestration of the sinusoidal endothelium occurs early in the pathogenesis of cirrhosis, both in humans exposed to hepatotoxins and in animal models of cirrhosis [43]. Correlating the outcome from current investigation and previous reports it could be ascertained that the further exposure to FPN dosage could probably incur the cirrhosis like condition in the exposed animal. In another study, authors have suggested the propensity of FPN and its metabolites in promoting adipogenesis [44]. Since FPN is found to be a lipophilic agent, its ability to accumulate in lipids cannot be overlooked [[45], [46]] since its effect in similar approach on certain organisms like earthworms are also quite evident [47] which has been evidenced by increase in body weight gain of the exposed animal. The rats under high dose group showed maximum damage with findings like necrosis, degeneration of bile duct and hepatocytes, impaired sinusoids and damaged portal vein were clearly visible. Changes in rats of medium dose group were found to be comparatively lesser. However, the intensity of damage was found to be more than that of rats under low dose group. The rats under medium dose group were characterized with changes like vacuolization, degenerated portal vein, pyknotic nucleus, dilated sinusoid, degeneration of hepatocytes and cytoplasmic degeneration. Stagnation of bile was noticed for high and medium doses. Our findings are in agreement with Kerem et al., [48], who as well reported that fenitrothion treated rats demonstrated similar histopathological alterations in liver which led to severe effects. Correlating the histoarchitectural findings with antioxidant outcome, it is ascertained that decline in enzymatic threshold of ROS scavenging enzymes might have triggered the oxidation reactions thereby causing the catastrophic damage to the cells and tissues [49].

Table 2

Histopathological changes in liver of male Wistar rats following oral exposure to different doses of FPN.

Findings	Groups
	Control	Exposed
		High	Medium	Low
Vacuolation (V)	ND	* *	* *	*
Dilated sinusoid (DS)	ND	* *	* *	ND
Hypertrophy of hepatocytes (H)	ND	* * *	* *	*
Stagnation of bile (B)	ND	*	**	ND
Damaged hepatic artery (HA)	ND	*	* *	ND
Degeneration/Clogging of bile duct (BD)	ND	* * * *	* * *	ND
Focal necrosis (F)	ND	*	ND	ND
Degenerated/Thrombosis/Clogged portal vein (PV)	ND	ND	ND	* * * *

Histopathological findings in the liver of male Wistar albino rats with different groups indicated, (ND) as Not detected, (*) as low, (* *) as medium, (* * *) as high and (* * * *) as severe levels of histoarchitectural damage.

Fig. 2

Photomicrograph showing sections of rat liver of Control (0.0 mg/kg BW/day) a: Hepatocytes (H), Portal Vein (PV), Blood sinusoids (BS), Hepatic Artery (HA), Bile Duct (BD), interlobular Connective Tissue; rats exposed to High dose (32.33 mg/kg BW/day) b: Damaged Bile Duct (BD), Ruptured Portal Vein (PV), dilated blood sinusoids (BS), Damaged Hepatic Artery (HA), Hypertrophy of Hepatocytes (H), Disrupted Connective Tissue (CT), Focal Necrosis (F); rats exposed to medium dose (12.12 mg/kg BW/day) c: Mild Dilation of Blood Sinusoids (BS), Partial clogging of Bile Duct (BD) and Portal Vein (PV), Damaged Hepatic Artery (HA) and Connective Tissue (CT), Hypertrophy of Hepatocytes (H), Stagnation of Bile (B), mild Vacuolation (V), Focal Necrosis (F); rats exposed to with low dose (6.46 mg/kg BW/day) d: Hypertrophy of Hepatocytes (H), Clogged Portal Vein (PV), (H and E staining, 200 X).

Fig. 3

Photomicrograph showing control and FPN exposed sections of rat liver; notice intact hepatocytes, blood sinusoids, portal vein, and bile duct in (a): Control (0.0 mg/kg BW/day); Degenerated hepatocytes, damaged portal vein, bile duct and necrotized area around portal vein (b): High dose- 32.33 mg/kg BW/day, c: Medium dose- 12.12 mg/kg BW/day and (d): Low dose- 6.46 mg/kg BW/day (H and E staining, processed with ImageJ, 200 X).

FT-IR analysis

The four mean normalized spectra corresponding to wavenumber 4000–500 cm−1 have been presented as control (curve 1), high (curve 2), medium (curve 3) and low dose (curve 4) groups of rat liver (Table 3; Fig. 4). The bands at 1654 and 1534 cm−1 correspond to amide I and II vibrations of structural proteins respectively, with the first band associated with protein amide C—O stretching vibration and second band corresponding to amide N—H bending vibration coupled to C—N stretching vibration of polypeptide and protein backbone [50]. The current outcome points to the possibilities of the antagonistic approach of FPN against membrane-bound lipids which are the primarily affected structures due to pesticide toxicity [51]. The observation supports the hypothesis that polyunsaturated fatty acids (PUFA) are particularly susceptible to hydrogen removal resulting in the initiation of a radical chain reaction [52]. An increase in the intensity of the carbonyl-stretching mode (1732 cm−1) may indicate an increase in the accumulation of lipids [53] which suggests the synthesis of lipids in excess due to FPN.

Table 3

General band assignments for FTIR spectra of the liver of rats under control and groups exposed to sublethal doses of FPN.

Peak	Groups				Assignments of peaks
	Control	Exposed
		High	Medium	Low
1	3406	3428	3413	3303	Amine N—H asymmetric stretching
2	2925	2924	2924	2924	CH3 asymmetric stretching: mainly lipids
3	2854	2855	2857	2854	CH2 asymmetric stretching: mainly lipids
4	1652	1642	1652	1654	Amide I: Protein C <svg xmlns="http://www.w3.org/2000/svg" version="1.0" width="20.666667pt" height="16.000000pt" viewBox="0 0 20.666667 16.000000" preserveAspectRatio="xMidYMid meet"><metadata> Created by potrace 1.16, written by Peter Selinger 2001-2019 </metadata><g transform="translate(1.000000,15.000000) scale(0.019444,-0.019444)" fill="currentColor" stroke="none"><path d="M0 440 l0 -40 480 0 480 0 0 40 0 40 -480 0 -480 0 0 -40z M0 280 l0 -40 480 0 480 0 0 40 0 40 -480 0 -480 0 0 -40z"/></g></svg> O stretching
5	1546	1550	1543	1545	Amide II: Protein N—H bending, C—N stretching
6	1454	1456	1452	1454	C—H bending (scissoring) (in CH3groups)/aromatic —CC stretching vibrations
7	1402	1383	1400	1399	–OH bending vibrations, —C—O—H in-plane bending vibrations,—CH3 out-of-plane bending vibrations, —CH2— wagging and twisting vibrations
8	1238	1268	1315	1315	C(O)—O stretching vibrations and —OH in plane vibrations/amide III (e.g. in aromatic ethers)
9	1149	1162	1241	1239	C—O stretching vibrations (e.g. in C—O—C glycosidic linkages of oligosaccharides or in triacylglycerols)
10	1079	1036	1080	1081	PO2− symmetric stretching: Phospholipids and nucleic acids
11	925	806	870	926	γzOH of carboxylic group

Fig. 4

Co-added and overlaid infrared spectra (4000–500 cm−1 spectral region) of liver tissue for the control (0.0) and groups treated with high (32.33), medium (12.12) and low (6.46 mg/kg BW) dose of FPN.

The stretch of 3500–2500 cm−1 with bands centred at 3300, 2990, 2925, and 2854 cm−1, corresponding to the stretching mode of OH and/or NH, H—CC—H, asymmetrical CH3, and both asymmetrical and symmetrical CH2 vibrations, respectively and were found to be affected significantly following the exposure to FPN under subchronic duration. The region corresponding to fatty acid has been highlighted in the current study as the FPN is found to be an adipogenic chemical as reported by Sun et al. [44]. A slight increase in the intensity of the band absorption pattern at 3406 cm−1 and a highly significant reduction (Table 4; Fig. 4) in the ratio of the absorption at 2924 cm−1 (CH3 asymmetric stretching vibration) to that at 2925 cm−1 (CH2 asymmetric and weak CH3 symmetric stretching vibrations) were observed. Moreover, it was noticed that a significant decrease from the control group to the treated one in the ratio of the peak area at 2854 cm−1 (CH2 asymmetric vibration) to that at 2855 and 2857 cm−1 (CH2 symmetric vibration) were witnessed in high and medium dose groups with rats under low dose remaining undisturbed. It is known that the symmetric CH2 stretching band at 2854 cm−1 is particularly valuable as a monitor for probing the “state of order” of biological membranes because its frequency and bandwidth parameters respond sensitively to order–disorder transitions and to changes in mobility of the fatty acid chains [54]. According to Liu et al. [55], “the main amide I absorption in infarcted tissue was shifted from 1650 to 1628 cm−1, a shift indicative of either a structural rearrangement of the existing tissue proteins or the expression of a new set of proteins with different structural characteristics”. This kind of outcome has been witnessed in the peak number 4 where in the variation was from 1652 to 1642, 1652 and 1654 cm−1 for high, medium and low doses respectively.

Table 4

Changes in the absorption of IR peaks in the liver of male Wistar rats following oral administration to different doses of FPN.

	Range	Groups
Peak		Control	Exposed
			High	Medium	Low
1	3303–3428	144.39	29.83	36.139	76.708
2	2924–2925	2.189	0.602	0.722	1.584
3	2854–2857	0.678	0.159	0.366	0.647
4	1642–1654	18.283	2.927	6.038	15.124
5	1543–1550	6.45	0.241	2.34	7.157
6	1452–1456	1.031	0.145	0.452	1.017
7	1383–1402	0.929	0.019	0.373	0.947
8	1268–1328	1.154	0.03	0.381	1.166
9	1156–1241	0.181	0.05	0.055	0.143
10	1036–1081	0.534	0.041	0.065	0.483
11	806–926	0.605	0.137	0.046	0.401

The bands observed at ∼1454, 1402, 1328, 1156, 1079 and 925 cm−1 are mainly due to C—H bending —OH bending vibrations C(O)–O stretching vibrations C—O stretching vibrations PO2− symmetric stretching and γzOH of the carboxylic group respectively were also found to be largely affected. The medium intensity band observed at ∼1235 cm−1 is that of the PO2-asymmetric stretching modes of the phosphodiester indication of phospholipids and the amide III/CH2 wagging vibration from the glycine backbone and protein side chain. Liver being the site of detoxification, is also known to maintain stable equilibrium through synthesis and degradation its glycogen [56]. Considering the involvement of polysaccharides, the band at 1081 cm−1 was more appropriate for study and is assigned as mainly to the C—O stretching vibrations of polysaccharides inclusive of glycogen component [57]. Cakmak et al. [58] had reported that the band observed at 1237 and 1235 cm−1 corresponds to PO2− asymmetric stretching of nucleic acids with little contribution from phospholipids and 1081 and 1082 cm−1 are mainly due to symmetric stretching of PO2− group in nucleic acids and phospholipids. All the band absorptions were found to decline and minimal absorption was observed for rats under low dose group which also suggested the decline in the concentration of membrane-bound lipids and damage to DNA as well.

Liver function test

In the current study, FPN caused a significant elevation in the levels of AST, ALT and ALP in the serum of rats (Table 5). The percent change noticed for AST was 184.79, 35.46 and 28.73% for high, medium and low dose respectively. ALT a pyridoxal phosphate-dependent enzyme of hepatic origin also showed an increase with percent change of 304.02, 82.46 and 46.39% for high, medium and low dose exposed groups. A Similar trend was noticed for ALP levels suggesting significantly elevated levels with percent change of 165.08% (high dose) followed by 124.42% (medium dose) and 10.64% (low dose) of FPN. The changes in levels of liver maker enzymes are often utilized as a crucial indicator of cellular damage among hepatocytes with a further indication of altered plasma membrane permeability [59]. Several reports have suggested similar findings wherein the increase in liver marker enzymes has been attributed to the histopathological incidence. Our results are in agreement with Celik et al. [60] who reported similar conditions of elevated ALT in the serum of rats following dichlorvos exposure.

Table 5

Changes in serum biochemical levels of wistar rats on exposure to selected doses of FPN.

Sl. No.	Parameter	Groups
		Control	Exposed
			High	Medium	Low
6.	Aspartate aminotransferase	85.01 ± 2.64	242.19 ± 2.22**	115.16 ± 1.47*	109.44 ± 1.44 *
7.	Alanine aminotransferase	55.37 ± 1.97	223.71 ± 2.64**	101.03 ± 2.46*	81.06 ± 0.91*
8.	Alkaline phosphatase	133.88 ± 2.42	354.91 ± 3.46**	300.46 ± 3.32**	148.13 ± 2.31*

Values represented in groups are means ± SE; significantly different from control.

p < 0.05.

p < 0.01.

The type of liver injury is associated with the relative rise of ALT and ALP is documented by Hussaini and Farrington [61]. A review made by Pandit et al. [62] suggests the elevated level of liver enzymes following administration of diclofenac. The ratio among the maker enzymes is also crucial for determining the type of injury. In ischemic or toxic liver injury, AST levels are found to peak and condition is known to progress even before those of ALT. The background of this process being the enzyme's peculiar intralobular distribution [63]. An additional investigation has suggested that the Zone 3 of the acinus is more vulnerable to both hypoxic (hepatocytes are exposed to an already oxygen-poor milieu) and toxic (hepatocytes are richer in microsomal enzymes) damage. Giannini et al. [12] opined similar changes in serum AST and emphasized that the hepatic damage could be either due ischemic or toxic nature of the compound. The present condition which was characterized by the elevation in AST levels of serum was a substantial evidence of damage to zone 3 of hepatic acinus and has been confirmed by histopathological analysis under current investigation.

Conclusion

Based on the overall findings from the present investigation, it may be inferred that FPN is toxic to liver following its ingestion at the selected doses for 90 days, as it is known to alter the biochemical levels with additionally conferring structural impairments as well. However, owing to the limitations of the current investigation, more studies are recommended to confirm the toxicity of low dose chosen under present study which showed ambiguous results for parameters considered. In addition to this, the endpoints obtained from the current investigation could be critically supportive in evaluating the changes under molecular levels. The study could be concluded by further cautioning the farming community about the hepatic damage upon intake of FPN.