Evaluation of Tramadol Hydrochloride Toxicity to Juvenile Zebraﬁsh—Morphological, Antioxidant and Histological Responses

: The presence of pharmaceuticals in water bodies is associated with the increasing consumption of these substances and limited elimination from wastewater. Pharmaceutical residues and their metabolites may have an unfavorable impact on ﬁsh and other aquatic biota. As the puriﬁcation of wastewater from tramadol is very limited and the knowledge on its e ﬀ ects on non-target organisms is low, we decided to assess the subchronic impact of tramadol hydrochloride on ﬁsh—on the mortality, growth and histopathology, together with the impact on selected indices of oxidative stress. The juvenile growth toxicity test was carried out on zebraﬁsh ( Danio rerio ), in accordance with the Organisation for European Economic Cooperation Guidelines 215 (Fish, Juvenile Growth Test). The ﬁsh were exposed to a range of tramadol hydrochloride concentrations (0.2, 2, 20, 200 and 600 µ g / L) for 28 days. The outcome of this study suggests that chosen concentrations of tramadol hydrochloride did not a ﬀ ect either mortality or growth (regarding weight, length and speciﬁc growth rate). However, the results of this study indicate that 28-day exposure can negatively inﬂuence selected indices of oxidative stress, which is a harmful imbalance between free radicals and antioxidants in an organism. A signiﬁcant increase was observed in glutathione S-transferase activity in the experimental group exposed to 2 µ g / L tramadol hydrochloride, compared to the control. Moreover, lipid peroxidation was observed in groups exposed to 20 and 200 µ g / L, in comparison to the control.


Introduction
In recent years, pharmaceuticals have become one of the most important environmental contaminants. Pharmaceuticals enter the aquatic environment as a consequence of their increasing use in human and veterinary medicine and incomplete removal during wastewater treatment processes [1][2][3][4][5].
at the age of 30 days, were chosen as the model organism for our study. This model organism belongs to the one of the most commonly used model species [29][30][31][32][33].
Moreover, the zebrafish is among the recommend organisms to perform Fish Juvenile Growth Test [28]. The fish used for the experiment were at the age of 30 days, as at this period of time, they were all considered to be at the juvenile stage [34].
Experimental organisms were exposed to a range of concentrations of tramadol hydrochloride (0.2, 2, 20, 200 and 600 µg/L). The duration of the subchronic toxicity test was 28 days. According to OECD guideline No. 215, five concentrations of the test substance are required. The two lowest concentrations were established with respect to the reported environmentally relevant concentration of this substance in surface water [7,23]. Additionally, 10×, 100× and 300× higher concentrations were also tested, in order to better understand the toxic effects of the substance tested.
The control and all experimental concentrations were tested in duplicate. The experiment was approved by the ethical committee of University of Veterinary and Pharmaceutical Sciences Brno (Czech Republic) and was in compliance with national legislation (Act No. 246/1992 Coll., on the Protection of Animals Against Cruelty, as amended, and Decree No. 419/2012 Coll., on the Protection, Breeding and Use of Experimental Animals, as amended).
A total of 600 fish were randomly divided into twelve 30-litre glass aquaria in dechlorinated tap water (50 in each aquarium). A toxicity test was performed in a flow-through system, with bath exchange every 12 h. Testing solutions of tramadol hydrochloride (chemical purity ≥ 99%, Sigma-Aldrich, Czech Republic) were prepared every day, and an ultrasonic bath was used to dissolve the substance. The initial body weight and total length were 11.34 ± 1.53 mg and 10.60 ± 4.83 mm (mean ± standard error of the mean), respectively. The fish were fed with commercial dried Artemia salina, without nutshells, at the total rate of 8% body weight. After fourteen days of toxicity test, the fish were weighed again, and the feed amount was recalculated. At the end of our experiment, the fish were euthanized (MS 222) and weighted, and their total lengths and tank-average specific growth rates (r) were determined.
During the toxicity tests, conditions, water quality and the number of dead fish were recorded in each aquarium, at 12-hour intervals. The values of water quality were as follows: temperature 25 ± 1 • C; oxygen saturation above 84 %; and pH from 7.94 to 8.24.

Histopathological Examination
Ten fish in each experimental group were used for histopathological examination. Fish were fixed in buffered 10% neutral formalin, dehydrated, embedded in paraffin wax, sectioned on a microtome at 4 µm and stained with hematoxylin and eosin. The qualitative histopathology analysis of selected tissues, such as gill, kidney, liver and intestine, was examined by light microscopy. Occurrence of abnormalities in experimental groups was compared to the control group.

Analysis of Selected Biomarkers in Whole-Body Homogenate
Whole-body homogenates were used for analysis of selected antioxidant enzymes (CAT, GR and GPx) [35][36][37], a detoxifying enzyme (GST) [38] and lipid peroxidation, using thiobarbituric acid (TBARS) [39]. At first, individual fish samples (ten in each experimental group) were mixed with phosphate buffer (pH 7.2) and homogenized (1:10; w/v). Lipid peroxidation was analyzed in pure homogenate. Enzyme analysis was performed in supernatant samples, which were obtained after centrifugation of homogenate (10,500 g, 4 • C, 20 min). All samples were immediately frozen and stored at -85 • C, until analysis. Analyses of all biomarkers were determined spectrophotometrically by a Varioskan Flash multimode microplate reader (Thermo Fisher Scientific, USA). Catalytic activities of all analyzed enzymes were normalized to protein concentration, determined by using bicinchoninic acid [40]. Amount of lipid peroxidation was expressed as nmol per gram wet weight of tissue.

Analysis of Tramadol Hydrochloride in Water
Tramadol hydrochloride was determined by high-performance liquid chromatography coupled with electrospray ionization-tandem mass spectrometry (HPLC-ESI-MS/MS). Water samples from each concentration were collected twice a day. Sample preparation included filtration through a 0.45 µm nylon filter (Millipore Billerica, MA), and a 10 µL aliquot of the final sample extract was injected. A Thermo Scientific HPLC Accela 1250 pump drew the mobile phase through a Hypersil C 18 column (2.1 mm × 50 mm, 1.9 µm), into a mass spectrometer, Thermo Fisher Scientific TSQ Quantum Access MAX Triple Quadrupole Instrument (Thermo Fisher Scientific, USA). The mobile phase consisted of 0.1 mol/L ammonium formate:acetonitrile (90:10;v/v). Mass spectrometer used electrospray ionization probe (ESI) for ionization of the samples ( Table 1). The ESI was operated in the positive-ion mode, under the following conditions: capillary temperature 375.0 • C; vaporizer temperature 300.0 • C; sheath gas pressure 35.0 psi; drying gas 10 a.u.; and capillary voltage 3500 V. The limit of detection was 0.145 µg/L. The internal standard was used as internal control.

Statistical Evaluation
Statistical evaluation was performed by using statistical software-Unistat for Excel 5.6 (Unistat Ltd., GB). At first, all data were tested for normal distribution, using the Shapiro-Wilk test, and for homogeneity of variance, using the Levene test. The one-way analysis of variance, followed by post hoc Dunnett's test, was used to determine the differences between the control and experimental groups. Level of significance was accepted at p < 0.05. All data are expressed as a mean ± standard deviation.

Mortality Rate
There was no increase in total cumulative mortality found between treated groups and the control. Among groups, mortality did not exceed 5% during the whole test. This result supports the finding from the previous study performed by Sehonova et al. [27], who tested similar concentrations of tramadol hydrochloride (from 10 to 200 µg/L) on zebrafish (Danio rerio) embryos and also on embryos and larvae of common carp (Cyprinus carpio). Likewise, Bachour et al. [26] did not record embryotoxicity of tramadol on zebrafish larvae. After 144 h of exposure (fish were exposed to tramadol concentrations from 24 to 6250 µg/L), no adverse impact of the tested substance was observed. Bachour et al. [26] also did not notice any effect, even after treatment with a mixture of tramadol and antidepressant citalopram. However, in a test performed by Sehonova et al. [12], where common carp embryos and larvae were exposed to a mixture of tramadol hydrochloride and naproxen sodium for a period of 32 days, increased mortality (50%) was already observed in the group of 200 µg/L.
Various authors have reported on the impact of tramadol on the behavior of aquatic organisms [14,15,26]. During our test, fish in all treated groups exhibited normal behavior. However, it is necessary to point out that monitoring of effects of tramadol on fish behavior was not the goal of our research, and thus no validated method on fish-behavior assessment was followed. Bachour et al. [26] monitored the swimming activity of zebrafish larvae and found out that a tramadol concentration of 320 µg/L had a significant anxiolytic effect (hypoactivity during dark conditions). Even lower concentrations can affect the behavior of some other aquatic organisms. An environmentally relevant concentration of tramadol (1 µg/L) caused crayfish to spend more time in shelters, and both their swimming velocity and swimming distance were affected [14,15].

Fish Growth
The effect of exposure of Danio rerio to tramadol hydrochloride on fish development is given in Table 2. Neither body weight at the beginning of the experiment nor body weight on last day of the experiment was found to be significantly different among groups. Similarly, no significant differences in average body weight, total length and specific growth rate were observed. In contrast, Sehonova et al. [27] reported inhibition of specific growth rate of common carp among groups exposed to tramadol. Carp larvae were also found to be significantly shorter after tramadol exposure (on day 28 and 32), with significantly lower body weight. Likewise, the inhibition of specific growth rate was found by Sehonova et al. [12], in groups exposed to a mixture of tramadol and naproxen, at the concentrations of 10, 50 and 100 µg/L. In contrast, higher body weight and significantly longer body were found after exposure to the highest tested concentration (200 µg/L) of tramadol and naproxen mixture. The authors discuss the possible effect of increased mortality in this group and, with it, related better life conditions of survivors compared to other groups (more space in the testing vessel and higher food availability). Moreover, Sehonova et al. [27] reported that tramadol exposure (including environmentally relevant concentration) caused a hatching delay in the fish embryos of both zebrafish and common carp.

Histopathology
As a result of our experiment, only histopathological changes in liver (abnormal glycogen accumulation) were observed among tested groups, apart from the lowest concentration of 0.2 µg/L ( Figure 1). In contrast, no histopathological changes in liver of common carp after tramadol hydrochloride exposure were described by Sehonova et al. [27].
No significant histological changes were observed in all analyzed organs (skin, gill, kidney and brain). In contrast, Sehonova et al. [27] described that histopathological examination of early life stages of common carp revealed gill hyperemia. They also noticed an increased number of the skin mucous cells of fish in tested groups. Comparably, similar findings have been published by Sehonova et al. [12], where no changes in liver after tramadol-and-naproxen-mixture exposure in early life stages of common carp were observed. Similarly, there was an elevated amount of skin mucous cells. In addition, histopathological examination showed deformations of gill lamellas.

Oxidative Stress Indices
The potentially negative impacts of zebrafish subchronic exposure to tramadol hydrochloride were also studied by conducting an analysis of selected oxidative stress indices. Most often, induction of oxidative stress in aquatic animals is assessed by using changes in various enzyme activities, which play crucial roles in antioxidant defense. The role of the first-line defense enzyme antioxidants is primarily provided by superoxide dismutase, CAT and GPx, which suppress or prevent the formation of free radicals or reactive species in cells. In the next defense line, the oxidized form of glutathione, created as a result of the reaction catalyzed by GPx, is regenerated to the reduced form of glutathione by GR [41][42][43]. An important enzyme in antioxidant protection is also multifunctional phase II biotransformation enzyme -GST, which is involved in the xenobiotic detoxification and in elimination of reactive oxygen species, as well as products of lipoperoxidation [44]. One of the significant manifestations of antioxidant defense disruption is lipid peroxidation, which is often used as a useful oxidative stress indicator [40].
In our study, changes in various antioxidant enzyme activities (CAT, GR, GPx and GST) and lipid peroxidation were evaluated. Obtained results are given in Figures 2-6. In our study, fish exposed to tramadol hydrochloride did not show any considerable changes in GR, GPx or CAT activities between control and experimental groups. Surprisingly, a significant increase in GST activity was recorded only at the concentration of 2 µg/L (p < 0.01), compared to the control group. No changes were recorded in higher concentrations. An increase in GST activity, mainly in low environmentally relevant concentrations, was also found by Zivna et al. [45]. They studied the effect of salicylic acid on zebrafish, after 28 days of exposure. An increase in activity of the detoxification

Oxidative Stress Indices
The potentially negative impacts of zebrafish subchronic exposure to tramadol hydrochloride were also studied by conducting an analysis of selected oxidative stress indices. Most often, induction of oxidative stress in aquatic animals is assessed by using changes in various enzyme activities, which play crucial roles in antioxidant defense. The role of the first-line defense enzyme antioxidants is primarily provided by superoxide dismutase, CAT and GPx, which suppress or prevent the formation of free radicals or reactive species in cells. In the next defense line, the oxidized form of glutathione, created as a result of the reaction catalyzed by GPx, is regenerated to the reduced form of glutathione by GR [41][42][43]. An important enzyme in antioxidant protection is also multifunctional phase II biotransformation enzyme -GST, which is involved in the xenobiotic detoxification and in elimination of reactive oxygen species, as well as products of lipoperoxidation [44]. One of the significant manifestations of antioxidant defense disruption is lipid peroxidation, which is often used as a useful oxidative stress indicator [40].
In our study, changes in various antioxidant enzyme activities (CAT, GR, GPx and GST) and lipid peroxidation were evaluated. Obtained results are given in Figures 2-6. In our study, fish exposed to tramadol hydrochloride did not show any considerable changes in GR, GPx or CAT activities between control and experimental groups. Surprisingly, a significant increase in GST activity was recorded only at the concentration of 2 µg/L (p < 0.01), compared to the control group. No changes were recorded in higher concentrations. An increase in GST activity, mainly in low environmentally relevant concentrations, was also found by Zivna et al. [45]. They studied the effect of salicylic acid on zebrafish, after 28 days of exposure. An increase in activity of the detoxification enzyme GST probably indicates an activation of antioxidant system against xenobiotic. A similar study was performed by Sehonova et al. [27]. They examined effects of tramadol hydrochloride on common carp (Cyprinus carpio) embryos and larvae. No changes in GR and GST activities after tramadol hydrochloride exposure were reported. In contrast, they observed a significant reduction in GPx activity at the highest concentrations of 100 and 200 µg/L of tramadol hydrochloride. Furthermore, Sehonova et al. [12] did not find differences in GR activity after exposure of a mixture of tramadol hydrochloride and naproxen sodium in common carp. They noticed a significant drop in GST activity, but only at a concentration of 100 µg/L. Likewise, they recorded a decrease in GPx activity among various groups exposed to a mixture of tramadol hydrochloride and naproxen sodium (50, 100 and 200 µg/L). enzyme GST probably indicates an activation of antioxidant system against xenobiotic. A similar study was performed by Sehonova et al. [27]. They examined effects of tramadol hydrochloride on common carp (Cyprinus carpio) embryos and larvae. No changes in GR and GST activities after tramadol hydrochloride exposure were reported. In contrast, they observed a significant reduction in GPx activity at the highest concentrations of 100 and 200 µg/L of tramadol hydrochloride. Furthermore, Sehonova et al. [12] did not find differences in GR activity after exposure of a mixture of tramadol hydrochloride and naproxen sodium in common carp. They noticed a significant drop in GST activity, but only at a concentration of 100 µg/L. Likewise, they recorded a decrease in GPx activity among various groups exposed to a mixture of tramadol hydrochloride and naproxen sodium (50, 100 and 200 µg/L).
The results of our study indicate a significant increase in lipid peroxidation after exposure to tramadol hydrochloride. In particular, TBARS levels were increased among groups in comparison to the control, but a statistically significant (p < 0.01) difference was observed only in concentrations of 20 and 200 µg/L of tramadol hydrochloride. Surprisingly, TBARS values were not significantly increased in the highest tested concentration, i.e., 600 µg/L. The explanation for these results might be, as suggested by Sehonova et al. [12], that higher concentrations of tramadol hydrochloride may induce an antioxidant effect.  enzyme GST probably indicates an activation of antioxidant system against xenobiotic. A similar study was performed by Sehonova et al. [27]. They examined effects of tramadol hydrochloride on common carp (Cyprinus carpio) embryos and larvae. No changes in GR and GST activities after tramadol hydrochloride exposure were reported. In contrast, they observed a significant reduction in GPx activity at the highest concentrations of 100 and 200 µg/L of tramadol hydrochloride. Furthermore, Sehonova et al. [12] did not find differences in GR activity after exposure of a mixture of tramadol hydrochloride and naproxen sodium in common carp. They noticed a significant drop in GST activity, but only at a concentration of 100 µg/L. Likewise, they recorded a decrease in GPx activity among various groups exposed to a mixture of tramadol hydrochloride and naproxen sodium (50, 100 and 200 µg/L).
The results of our study indicate a significant increase in lipid peroxidation after exposure to tramadol hydrochloride. In particular, TBARS levels were increased among groups in comparison to the control, but a statistically significant (p < 0.01) difference was observed only in concentrations of 20 and 200 µg/L of tramadol hydrochloride. Surprisingly, TBARS values were not significantly increased in the highest tested concentration, i.e., 600 µg/L. The explanation for these results might be, as suggested by Sehonova et al. [12], that higher concentrations of tramadol hydrochloride may induce an antioxidant effect.     Appl. Sci. 2020, 10, x FOR PEER REVIEW 8 of 11 Figure 3. Analysis of glutathione peroxidase activity (GPx) Data are expressed as mean ± standard deviation. No significant differences (p > 0.05) were found between control and experimental groups.   The results of our study indicate a significant increase in lipid peroxidation after exposure to tramadol hydrochloride. In particular, TBARS levels were increased among groups in comparison to the control, but a statistically significant (p < 0.01) difference was observed only in concentrations of 20 and 200 µg/L of tramadol hydrochloride. Surprisingly, TBARS values were not significantly increased in the highest tested concentration, i.e., 600 µg/L. The explanation for these results might be, as suggested by Sehonova et al. [12], that higher concentrations of tramadol hydrochloride may induce an antioxidant effect. Figure 6. Analysis of thiobarbituric acid reactive substance levels (TBARS). Data are expressed as mean ± standard deviation. Significant differences between control and experimental groups are indicated by ** (p < 0.01).

Conclusions
Since the purification of wastewater from tramadol is not perfect and the knowledge on its effects on non-target organisms is limited, we decided to assess the long-term impact of tramadol hydrochloride on survival, development and histopathology of juvenile zebrafish (Danio rerio), as well as the effects on selected indices of oxidative stress, represented by changes in GST, GR, GPx and CAT activity, and formation of lipid peroxidation products (TBARS).
The results of this study indicate that 28-day exposure can negatively influence selected indices of oxidative stress. A significant increase was observed in GST activity in the experimental group exposed to 2 µg/L, as compared to the control group. Moreover, increases in lipid peroxidation were observed in groups exposed to 20 and 200 µg/L, in comparison to the control group. Only slight changes in liver tissue were revealed by histopathological examination. On the contrary, not any of our tested concentrations of tramadol hydrochloride affected fish mortality, growth and activities of antioxidant enzymes, such as GR, GPx and CAT.

Conclusions
Since the purification of wastewater from tramadol is not perfect and the knowledge on its effects on non-target organisms is limited, we decided to assess the long-term impact of tramadol hydrochloride on survival, development and histopathology of juvenile zebrafish (Danio rerio), as well as the effects on selected indices of oxidative stress, represented by changes in GST, GR, GPx and CAT activity, and formation of lipid peroxidation products (TBARS).
The results of this study indicate that 28-day exposure can negatively influence selected indices of oxidative stress. A significant increase was observed in GST activity in the experimental group exposed to 2 µg/L, as compared to the control group. Moreover, increases in lipid peroxidation were observed in groups exposed to 20 and 200 µg/L, in comparison to the control group. Only slight changes in liver tissue were revealed by histopathological examination. On the contrary, not any of our tested concentrations of tramadol hydrochloride affected fish mortality, growth and activities of antioxidant enzymes, such as GR, GPx and CAT.
Author Contributions: L.P., performing of experiment and preparing of manuscript; P.S., analysis of oxidative stress indices; J.B., statistical analysis; V.D., analysis of tramadol hydrochloride in water samples; F.T. histopathological analysis; C.F., supervisor of experiment; P.B., performing of experiment; Z.S., preparing of manuscript. All authors have read and agreed to the published version of the manuscript.
Funding: This research received no external funding.