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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Immunol.</journal-id>
<journal-title>Frontiers in Immunology</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Immunol.</abbrev-journal-title>
<issn pub-type="epub">1664-3224</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fimmu.2024.1478114</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Immunology</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Effects of prolonged oxytetracycline supplementation on freshwater stinging catfish (<italic>Heteropneustes fossilis</italic>): a multi-biomarker approach</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Choudhary</surname>
<given-names>Pushpa</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/2614957"/>
<role content-type="https://credit.niso.org/contributor-roles/methodology/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-original-draft/"/>
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<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Naik</surname>
<given-names>Saisweta P.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/investigation/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Sahoo</surname>
<given-names>Sameer Ranjan</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/investigation/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Das</surname>
<given-names>Rakesh</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/697790"/>
<role content-type="https://credit.niso.org/contributor-roles/validation/"/>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Sahoo</surname>
<given-names>Satya Narayan</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/data-curation/"/>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Panda</surname>
<given-names>Satyen Kumar</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/data-curation/"/>
<role content-type="https://credit.niso.org/contributor-roles/methodology/"/>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Abraham</surname>
<given-names>Thangapalam Jawahar</given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/1819028"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Patil</surname>
<given-names>Prasanna Kumar</given-names>
</name>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/funding-acquisition/"/>
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</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Swain</surname>
<given-names>Priyabrat</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
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<contrib contrib-type="author" corresp="yes">
<name>
<surname>Mishra</surname>
<given-names>Sudhansu Sekhar</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/funding-acquisition/"/>
<role content-type="https://credit.niso.org/contributor-roles/project-administration/"/>
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</contrib-group>
<aff id="aff1">
<sup>1</sup>
<institution>Indian Council of Agriculture Research (ICAR)-Central Institute of Freshwater Aquaculture (CIFA), Fish Health Management Division</institution>, <addr-line>Bhubaneswar, Odisha</addr-line>, <country>India</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Fish Processing Division, Indian Council of Agriculture Research (ICAR)-Central Institute of Fisheries Technology</institution>, <addr-line>Cochin, Kerala</addr-line>, <country>India</country>
</aff>
<aff id="aff3">
<sup>3</sup>
<institution>Department of Aquatic Animal Health, Faculty of Fishery Sciences, West Bengal University of Animal and Fishery Sciences</institution>, <addr-line>Kolkata, West Bengal</addr-line>, <country>India</country>
</aff>
<aff id="aff4">
<sup>4</sup>
<institution>Indian Council of Agricultural Research (ICAR)-Central Institute of Brackishwater Aquaculture (CIBA), Aquatic Animal Health and Environment Division</institution>, <addr-line>Chennai, Tamil Nadu</addr-line>, <country>India</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>Edited by: Shimaa E. Ali, Norwegian Veterinary Institute (NVI), Norway</p>
</fn>
<fn fn-type="edited-by">
<p>Reviewed by: Guan-Jun Yang, Ningbo University, China</p>
<p>Sumanta Kumar Mallik, Directorate of Cold Water Fisheries Research (ICAR), India</p>
</fn>
<fn fn-type="corresp" id="fn001">
<p>*Correspondence: Sudhansu Sekhar Mishra, <email xlink:href="mailto:ssmishra60@gmail.com">ssmishra60@gmail.com</email>; Priyabrat Swain, <email xlink:href="mailto:pswainy2k@yahoo.co.in">pswainy2k@yahoo.co.in</email>
</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>19</day>
<month>12</month>
<year>2024</year>
</pub-date>
<pub-date pub-type="collection">
<year>2024</year>
</pub-date>
<volume>15</volume>
<elocation-id>1478114</elocation-id>
<history>
<date date-type="received">
<day>09</day>
<month>08</month>
<year>2024</year>
</date>
<date date-type="accepted">
<day>20</day>
<month>11</month>
<year>2024</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2024 Choudhary, Naik, Sahoo, Das, Sahoo, Panda, Abraham, Patil, Swain and Mishra</copyright-statement>
<copyright-year>2024</copyright-year>
<copyright-holder>Choudhary, Naik, Sahoo, Das, Sahoo, Panda, Abraham, Patil, Swain and Mishra</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p>
</license>
</permissions>
<abstract>
<sec>
<title>Background</title>
<p>Aquaculture systems that sporadically depend on antibiotics can contribute to the development of adverse effects on the fish, microbial flora and the environment. This study sought to investigate the impacts of extended oxytetracycline supplementation on the freshwater stinging catfish <italic>Heteropneustes fossilis</italic> through a multi-biomarker approach.</p>
</sec>
<sec>
<title>Methods</title>
<p>A total of 300 <italic>H. fossilis</italic> (20 &#xb1; 0.5&#xa0;g) were placed in fibreglass-reinforced plastic tanks. The experimental fish were administered oxytetracycline hydrochloride (OTC) at varying doses, viz., 80 mg/kg fish biomass/day (1x), 240 mg (3x), 400 mg (5x), and 800 mg (10x) for 30 consecutive days. The study also included a control group that did not receive OTC.</p>
</sec>
<sec>
<title>Results</title>
<p>OTC was effective against <italic>Aeromonas hydrophila</italic>, <italic>Pseudomonas putida</italic>, and <italic>Plesiomonas shigelloides</italic>, with minimum inhibitory concentrations ranging between 0.5 and 8.0 &#xb5;g/mL. The OTC supplementation retarded the growth of fish. The respiratory burst activity, myeloperoxidase, and lysozyme increased significantly in the 1x group until day 20. This group showed an increase in serum albumin, whereas other OTC groups exhibited elevated levels of liver functional enzymes, including alanine transaminase, aspartate aminotransferase, and alkaline phosphatase. In addition, OTC groups exhibited increased levels of antioxidant enzymes. The magnitude of the increase was dose- and time-dependent. The liquid chromatography-mass spectrometry/mass spectrometry (LC-MS/MS) study signified a dose-dependent increase in OTC residues in the muscle. After a 10-day discontinuation of OTC, the tissue level retention of residues was minimal in the muscle, specifically in the 1x group compared to other groups. Significant histological alterations were noted in the liver tissues of the 5x and 10x groups, possibly due to oxidative stress and residue accretion.</p>
</sec>
<sec>
<title>Conclusion</title>
<p>The therapeutic dose of 80 mg/kg biomass/day was safe and tolerated well by <italic>H. fossilis</italic>, and may be used for sustainable catfish farming practices.</p>
</sec>
</abstract>
<kwd-group>
<kwd>aquaculture</kwd>
<kwd>
<italic>Heteropneustes fossilis</italic>
</kwd>
<kwd>oxytetracycline hydrochloride</kwd>
<kwd>immunological indices</kwd>
<kwd>biochemical parameters</kwd>
<kwd>tissue level retention</kwd>
</kwd-group>
<contract-sponsor id="cn001">Indian Council of Agricultural Research<named-content content-type="fundref-id">10.13039/501100001503</named-content>
</contract-sponsor>
<counts>
<fig-count count="5"/>
<table-count count="3"/>
<equation-count count="0"/>
<ref-count count="53"/>
<page-count count="12"/>
<word-count count="4593"/>
</counts>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-in-acceptance</meta-name>
<meta-value>Comparative Immunology</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1">
<title>Highlights</title>
<list list-type="bullet">
<list-item>
<p>Effect of oxytetracycline (OTC) on <italic>Heteropneustes fossilis</italic> was evaluated</p>
</list-item>
<list-item>
<p>OTC caused dose- and time-dependent changes in immune and biochemical parameters</p>
</list-item>
<list-item>
<p>OTC effectively inhibited the bacterial fish pathogens</p>
</list-item>
<list-item>
<p>Higher OTC doses caused oxidative stress and impaired liver tissue histoarchitecture</p>
</list-item>
<list-item>
<p>LC-MS/MS analysis showed dose-dependent OTC accumulation in edible muscle</p>
</list-item>
</list>
</sec>
<sec id="s2" sec-type="intro">
<title>Introduction</title>
<p>More innovative practices have replaced extensive traditional aquaculture practices in recent decades. These practices involve raising aquatic animals at high stocking densities, which increases the crowding stress and lowers immunity in reared animals. This, in turn, increases the risk of the emergence of new diseases, leading to financial difficulties and unsustainable fish farming (<xref ref-type="bibr" rid="B1">1</xref>). Among numerous devastating emerging fish diseases, bacterial infections are one of the important culprits for successful aquafarming (<xref ref-type="bibr" rid="B2">2</xref>). Ideally, fish farmers treat bacterial pathogens through medicated feed supplemented with desired levels of antibiotics for a prescribed period (<xref ref-type="bibr" rid="B3">3</xref>&#x2013;<xref ref-type="bibr" rid="B5">5</xref>). Fish farmers often apply high doses of antibiotics for extended duration due to a lack of awareness on the impact of antibiotics (<xref ref-type="bibr" rid="B3">3</xref>), hence such a practice jeopardizes the safety of reared animals and end consumers. This injudicious use of antibiotics affects international trade and the aquatic environments (<xref ref-type="bibr" rid="B6">6</xref>). Research on the antibiotics that stay in fish muscle after long-term administration to treat bacterial diseases is the most important thing that necessitates the safe and wise use of antibiotics and the safety of aquatic products.</p>
<p>Oxytetracycline (OTC), an important antibiotic from the tetracycline group authorized for aquaculture use, is effective against the treatment of numerous bacterial pathogens (<xref ref-type="bibr" rid="B7">7</xref>), which works on the principle of inhibition of protein synthesis for bacterial lysis (<xref ref-type="bibr" rid="B8">8</xref>). However, studies have shown that it can hurt the fish liver and kidneys, change the microbiome of the gut, damage mitochondria, and make membrane lipid peroxidation worse (<xref ref-type="bibr" rid="B9">9</xref>, <xref ref-type="bibr" rid="B10">10</xref>). Therefore, ensuring the biosafety of OTC in cultured aquatic animals is critical before advocating its widespread use. Environmental conditions significantly influence the efficacy of antimicrobials (<xref ref-type="bibr" rid="B11">11</xref>), with factors such as water temperature affecting fish metabolism due to their poikilothermic nature. Compliance with regional antimicrobial regulations, drug depletion studies, and dose-response analyses under specific environmental conditions are essential. Despite established guidelines for temperate fish species, there is a lack of information on OTC safety, efficacy, and residue accumulation in tropical regions (<xref ref-type="bibr" rid="B11">11</xref>). Recent studies have looked at how safe OTC is for fish species like rohu (<xref ref-type="bibr" rid="B12">12</xref>), snubnose pompano (<xref ref-type="bibr" rid="B13">13</xref>), Nile tilapia (<xref ref-type="bibr" rid="B14">14</xref>), striped catfish (<xref ref-type="bibr" rid="B15">15</xref>), mrigal (<xref ref-type="bibr" rid="B16">16</xref>), and catla (<xref ref-type="bibr" rid="B17">17</xref>).</p>
<p>Asian stinging catfish <italic>Heteropneustes fossilis</italic> is among the most extensively farmed freshwater omnivorous catfish of the Heteropneustidae family. Highly valued for its culinary appeal, low-fat content, high protein content, and medicinal properties (<xref ref-type="bibr" rid="B18">18</xref>, <xref ref-type="bibr" rid="B19">19</xref>), this species thrives in challenging environments such as muddy waters with low oxygen levels. Its ability to tolerate prolonged periods of low oxygen and high ammonia concentrations further enhances its suitability for aquaculture, including stagnant water bodies like swamps and wetlands (<xref ref-type="bibr" rid="B20">20</xref>). To date, no study has investigated the impact of prolonged use of oxytetracycline hydrochloride (OTC) at gradually increasing doses through feed in <italic>H. fossilis</italic>. This study aimed to conduct a 30-day indoor in-feed OTC feeding trial at varying doses ranging from the therapeutic dose of OTC (1x; 80 mg/kg fish biomass/day) to 10 times the therapeutic dose (10x: 800 mg/kg fish biomass/day) and to explore the effects of OTC on non-specific immunity, serum biochemistry, oxidative stress biomarkers, residue retention in the edible muscle and liver histopathological alterations. Besides, the minimum inhibitory concentration (MIC) of OTC against common bacterial fish pathogens was determined to develop appropriate strategies on the dose and dosage, ensuring its sparing and responsible use in catfish aquaculture.</p>
</sec>
<sec id="s3" sec-type="materials|methods">
<title>Materials and method</title>
<sec id="s3_1">
<title>Animal ethics</title>
<p>Experimental trials were carried out in the wet laboratory at the Fish Health Management Division of the ICAR-Central Institute of Freshwater Aquaculture, (ICAR-CIFA) Bhubaneswar, India. The experiments were completed under the guidelines provided in ARRIVE (<xref ref-type="bibr" rid="B21">21</xref>) and the ethical committee of ICAR-CIFA, Bhubaneswar. All the methods and procedures of the All-India Network Project on Fish Health were endorsed by the Indian Council of Agricultural Research, Government of India, New Delhi (CIBA/AI-NPFH/2020-2025). Every procedure was as per the humane condition to reduce any sort of trouble to the experimental animals.</p>
</sec>
<sec id="s3_2">
<title>Determination of minimum inhibitory concentration of OTC against fish pathogens</title>
<p>The MIC of OTC against 8 fish pathogenic bacterial strains comprising four <italic>Aeromonas hydrophila</italic> and two each of <italic>Pseudomonas putida</italic> and <italic>Plesiomonas shigelloides</italic> was evaluated following the microplate broth dilution method (<xref ref-type="bibr" rid="B22">22</xref>).</p>
</sec>
<sec id="s3_3">
<title>Experimental conditions, setup and medicated feed preparation</title>
<p>A total of 300 stinging catfish devoid of any infections were sourced from local farmers near ICAR-CIFA, Kausalyaganga, Bhubaneswar, and acclimatized for three weeks in 1000 L fibreglass-reinforced plastic (FRP) tanks. The incorporation of OTC (Sigma-Aldrich, USA) into the basal diet was based on fish biomass as per the therapeutic dose of 80 mg/kg biomass/day (<xref ref-type="bibr" rid="B7">7</xref>). The experimental feeding trial included four treatment groups, in triplicates, with 20 fish in each tank, i.e., 1x (80 mg), 3x (240 mg), 5x (400 mg), and 10x (800 mg), as well as a control group with no OTC. The feed formulation involved essential nutrient inclusion with a basic protein content of 300 g/kg for the basal feed. OTC was added according to treatment specifications. The ingredients were accurately weighed, mixed, and pressure-cooked for 20 minutes to improve palatability. Afterwards, thoroughly blended the mineral and vitamin mix and the required amount of OTC were mixed with the cooked dough (<xref ref-type="table" rid="T1">
<bold>Table&#xa0;1</bold>
</xref>). A hand pelletizer was used to shape the dough into 2&#xa0;mm feed crumbles, dried in a hot air oven at 40&#xb0;C for 48&#xa0;h. The dried crumbles were stored in a zip lock polythene pouch at 4&#xb0;C. The experiment spanned 40 days comprised of 30 days of OTC administration at graded doses as above and 10 days of post-OTC-administration. The fish groups were fed appropriate feeds daily at 3% body weight twice daily in equal rations. The water quality parameters such as temperature (28.5 - 29&#xb0;C), pH (7.8 - 8.4), dissolved oxygen (5.1 - 5.7 mg/L), total alkalinity (121 - 134 mg/L), total ammonia nitrogen (0.44 - 0.87 mg/L), nitrate (0.75 - 0.95 mg/L, and nitrite (0.31 - 0.85 mg/L) were maintained optimally throughout the experiment.</p>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>Composition of medicated feed (gram/kg feed).</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="top" align="center">Ingredients</th>
<th valign="top" align="center">Control<break/>(Basal diet)</th>
<th valign="top" align="center">T1<break/>(80 mg/kg biomass/day)</th>
<th valign="top" align="center">T2<break/>(240 mg/kg biomass/day)</th>
<th valign="top" align="center">T3<break/>(400 mg/kg biomass/day)</th>
<th valign="top" align="center">T4<break/>(800 mg/kg biomass/day)</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="center">Fish meal</td>
<td valign="top" align="center">50</td>
<td valign="top" align="center">50</td>
<td valign="top" align="center">50</td>
<td valign="top" align="center">50</td>
<td valign="top" align="center">50</td>
</tr>
<tr>
<td valign="top" align="center">Soya meal</td>
<td valign="top" align="center">280</td>
<td valign="top" align="center">280</td>
<td valign="top" align="center">280</td>
<td valign="top" align="center">280</td>
<td valign="top" align="center">280</td>
</tr>
<tr>
<td valign="top" align="center">Ground nut oil cake</td>
<td valign="top" align="center">260</td>
<td valign="top" align="center">260</td>
<td valign="top" align="center">260</td>
<td valign="top" align="center">260</td>
<td valign="top" align="center">260</td>
</tr>
<tr>
<td valign="top" align="center">Rice bran</td>
<td valign="top" align="center">200</td>
<td valign="top" align="center">200</td>
<td valign="top" align="center">200</td>
<td valign="top" align="center">200</td>
<td valign="top" align="center">200</td>
</tr>
<tr>
<td valign="top" align="center">Corn flour</td>
<td valign="top" align="center">150</td>
<td valign="top" align="center">147.34</td>
<td valign="top" align="center">142</td>
<td valign="top" align="center">136.7</td>
<td valign="top" align="center">123.4</td>
</tr>
<tr>
<td valign="top" align="center">Oil</td>
<td valign="top" align="center">40</td>
<td valign="top" align="center">40</td>
<td valign="top" align="center">40</td>
<td valign="top" align="center">40</td>
<td valign="top" align="center">40</td>
</tr>
<tr>
<td valign="top" align="center">Vitamin and mineral mix</td>
<td valign="top" align="center">20</td>
<td valign="top" align="center">20</td>
<td valign="top" align="center">20</td>
<td valign="top" align="center">20</td>
<td valign="top" align="center">20</td>
</tr>
<tr>
<td valign="top" align="center">OTC</td>
<td valign="top" align="center">
<bold>0</bold>
</td>
<td valign="top" align="center">
<bold>2.66</bold>
</td>
<td valign="top" align="center">
<bold>8.0</bold>
</td>
<td valign="top" align="center">
<bold>13.3</bold>
</td>
<td valign="top" align="center">
<bold>26.6</bold>
</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>OTC, Oxytetracycline hydrochloride.* As in case of T1, 1 kg biomass was provided with 30 gm of medicated feed (3% BW/day), that contained 80 mg OTC.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="s3_4">
<title>Blood, serum and liver tissue collection</title>
<p>Every ten days, six fish were randomly picked from each treatment group (2 fish/tank) for the collection of blood, serum, edible muscle and liver tissues. Before collecting blood, 50 &#xb5;L/L of clove oil was applied as a fish sedative. Blood was collected from the caudal peduncle using a single-use 2.0 mL syringe and a portion was transferred to EDTA-coated vials for the assessment of respiratory burst activity (RBA). To separate serum, the entire blood without anticoagulant was held in a 1.5 mL microcentrifuge tube in a slanting position for one hour followed by 4 hours of incubation at 4&#xb0;C. The serum was separated by centrifugation at 3000&#xa0;g for 10&#xa0;min in a refrigerated centrifuge (Multifuge X1R, Thermo Scientific, USA) and stored at -20&#xb0;C until use. The humanely euthanized fish using clove oil (100 &#xb5;L/L) was carefully dissected, to remove the liver of each fish, The liver tissues were blended using a homogenizer (Qiagen Hilden, Germany) set to run at 8000 rpm for 30 sec with chilled 0.05 M tris-hydrochloride (pH: 8.0). The homogenate was centrifuged at 13,000 g at 4&#xb0;C for 15&#xa0;min to extract tissue fragments and lipids, transferred to the 1.5 mL Eppendorf vials and stored at -20&#xb0;C until the enzymatic testing.</p>
</sec>
<sec id="s3_5">
<title>Immunological and serum biochemical parameters</title>
<p>Blood RBA and serum myeloperoxidase (MPO) were assessed as previously described (<xref ref-type="bibr" rid="B23">23</xref>, <xref ref-type="bibr" rid="B24">24</xref>). The serum lysozyme was determined by following the (<xref ref-type="bibr" rid="B25">25</xref>) method. Serum albumin was measured by bromocresol green binding using an albumin kit (Coral Clinical Systems, India). The serum glucose, alanine transaminase (ALT), aspartate aminotransferase (AST), and alkaline phosphatase (ALP) were estimated according to the kit&#x2019;s instructions manufactured by Coral Clinical Systems, India.</p>
</sec>
<sec id="s3_6">
<title>Oxidative stress biomarkers in liver tissue</title>
<p>The activity of liver SOD was measured based on a cytochrome C reduction test utilizing a commercial kit (Cayman Chemicals, India), with absorbance obtained at 550 nm (<xref ref-type="bibr" rid="B26">26</xref>). CAT activity was evaluated using a commercial kit to break down hydrogen peroxide (<xref ref-type="bibr" rid="B27">27</xref>). Malondialdehyde (MDA) was assessed using a colourimetric approach based on the thiobarbituric acid reaction, calculated using commercial kits (Cayman Chemicals, India) as previously described (<xref ref-type="bibr" rid="B26">26</xref>)</p>
</sec>
<sec id="s3_7">
<title>Analysis of oxytetracycline residues in edible muscle tissue</title>
<p>To quantify OTC residues in edible muscle tissue, a brief modification of the method as illustrated (<xref ref-type="bibr" rid="B12">12</xref>) was employed. Approximately 15&#xa0;g of pooled tissue from two fish/tank on days 10, 20, and 30 of OTC-dosing, and day 10 post-OTC-dosing (40<sup>th</sup> day of the experiment) were individually homogenized. Each homogenate (approx. 5.0-6.0&#xa0;g) was mixed in a 50 mL falcon tube containing 20 mL of acetone and centrifuged at 8000&#xa0;g for 15&#xa0;min, resulting supernatant was transferred to a 100 mL round bottom flask and subjected to a second extraction with 10 mL of acetone. A rotary evaporator (Heidolph Laborota 4000, Germany) was used for concentrating total supernatants for removing acetone so that an aqueous solution could be obtained. The aqueous eluate was then chromatographically separated and collected. Following evaporation with a rotary evaporator, the eluate was dissolved in 2 mL of acetonitrile containing 1% acetic acid. Subsequently, 5 &#x3bc;L of the resulting solution was injected into an LC-MS/MS instrument for quantification of OTC, which exhibited a retention time of approximately 5&#xa0;min.</p>
</sec>
<sec id="s3_8">
<title>Liver histopathology</title>
<p>On days 10, 20, 30, and 40 of the experiment, a portion of liver tissues from each fish (six fish/group) was preserved in 10% neutral buffered formalin, followed by tissue processing and paraffin wax embedding. Wax blocks were subjected to a microtoming process to create 5.0 &#xb5;m tissue sections, thereafter stained with haematoxylin and eosin (<xref ref-type="bibr" rid="B28">28</xref>), and observed under a microscope (Olympus, Japan) for documentation of tissue alterations.</p>
</sec>
<sec id="s3_9">
<title>Statistical analysis</title>
<p>All the data were analyzed using the statistical package (SPSS Inc, USA, IBM) and represented as mean with standard deviation. The homogeneity of variances in the data was checked using Levene&#x2019;s test. One-way analysis of variance and Duncan&#x2019;s multiple range test were used to determine the significance at P&lt;0.05 among treatments and control.</p>
</sec>
</sec>
<sec id="s4" sec-type="results">
<title>Results</title>
<sec id="s4_1">
<title>MIC of OTC against fish pathogens</title>
<p>The MICs of OTC against common freshwater fish pathogenic strains such as <italic>A. hydrophila P. putida</italic> and <italic>P. shigelloides</italic> were in the range of 0.5&#x2013;8.0 &#xb5;g/mL (<xref ref-type="table" rid="T2">
<bold>Table&#xa0;2</bold>
</xref>).</p>
<table-wrap id="T2" position="float">
<label>Table&#xa0;2</label>
<caption>
<p>Minimal inhibitory concentration (MIC) of oxytetracycline against fish pathogenic bacterial strains.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="top" align="center">Bacterial species</th>
<th valign="top" align="center">Strain code</th>
<th valign="top" align="center">Tissue source</th>
<th valign="top" align="center">Fish species</th>
<th valign="top" align="center">Year of isolation</th>
<th valign="top" align="center">MIC (&#x3bc;g/mL)</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" rowspan="4" align="center">
<italic>Aeromonas hydrophila</italic>
</td>
<td valign="top" align="center">CIFA/AHy-03</td>
<td valign="top" align="center">Kidney</td>
<td valign="top" align="center">
<italic>Labeo rohita</italic>
</td>
<td valign="top" align="center">2021</td>
<td valign="top" align="center">0.5</td>
</tr>
<tr>
<td valign="top" align="center">CIFA/AHy-07</td>
<td valign="top" align="center">Blood</td>
<td valign="top" align="center">
<italic>Anabas testudineus</italic>
</td>
<td valign="top" align="center">2019</td>
<td valign="top" align="center">2.0</td>
</tr>
<tr>
<td valign="top" align="center">CIFA/AHy-14</td>
<td valign="top" align="center">Ulcer</td>
<td valign="top" align="center">
<italic>Catla catla</italic>
</td>
<td valign="top" align="center">2020</td>
<td valign="top" align="center">2.0</td>
</tr>
<tr>
<td valign="top" align="center">CIFA/AHy-15</td>
<td valign="top" align="center">Kidney</td>
<td valign="top" align="center">
<italic>H. fossilis</italic>
</td>
<td valign="top" align="center">2023</td>
<td valign="top" align="center">1.0</td>
</tr>
<tr>
<td valign="middle" rowspan="2" align="center">
<italic>Pseudomonas putida</italic>
</td>
<td valign="top" align="center">CIFA/PPu-05</td>
<td valign="top" align="center">Blood</td>
<td valign="top" align="center">
<italic>H. fossilis</italic>
</td>
<td valign="top" align="center">2022</td>
<td valign="top" align="center">0.5</td>
</tr>
<tr>
<td valign="top" align="center">CIFA/PPu-15</td>
<td valign="top" align="center">Liver</td>
<td valign="top" align="center">
<italic>H. fossilis</italic>
</td>
<td valign="top" align="center">2022</td>
<td valign="top" align="center">8.0</td>
</tr>
<tr>
<td valign="middle" rowspan="2" align="center">
<italic>Plesiomonas shigeloides</italic>
</td>
<td valign="top" align="center">CIFA/PSh-01</td>
<td valign="top" align="center">Kidney</td>
<td valign="top" align="center">
<italic>H. fossilis</italic>
</td>
<td valign="top" align="center">2023</td>
<td valign="top" align="center">2.0</td>
</tr>
<tr>
<td valign="top" align="center">CIFA/PSh-06</td>
<td valign="top" align="center">Blood</td>
<td valign="top" align="center">
<italic>H. fossilis</italic>
</td>
<td valign="top" align="center">2023</td>
<td valign="top" align="center">1.0</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s4_2">
<title>Fish biomass and non-specific immunity</title>
<p>The body weight of the OTC-fed (1x-10x) and control groups did not differ significantly during the feeding trial. Both the control and treatment groups documented 100% survival. Only the higher-dosed groups (5x and 10x) showed distinct behaviour abnormalities. The results of the non-specific immune parameters such as RBA, MPO, and lysozyme at different time points are shown in <xref ref-type="fig" rid="f1">
<bold>Figures&#xa0;1A&#x2013;C</bold>
</xref>. On the 10th and 20th day, the RBA and MPO increased significantly (<italic>p</italic>&lt;0.05) in the 1x group compared to the control and then reduced on the 30th day of OTC administration. Further, the other OTC doses insignificantly reduced the RBA, MPO, and lysozyme on the 30<sup>th</sup> day of administration. The lysozyme was elevated on the 10<sup>th</sup> day in the 1x and 3x groups, while in other OTC groups, it decreased (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1C</bold>
</xref>). On day 10 post-administration, elevated RBA, MPO and lysozyme levels were observed in comparison to the control.</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>
<bold>(A)</bold> Respiratory burst activity, <bold>(B)</bold> Myeloperoxidase activity and <bold>(C)</bold> Lysozyme activity of <italic>H</italic>. <italic>fossilis</italic> in the control and treated groups. Error bars with different alphabets on a specific day indicated significant differences (<italic>p</italic> &lt;&#x2009;0.05) among groups. OD, Optical density.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fimmu-15-1478114-g001.tif"/>
</fig>
</sec>
<sec id="s4_3">
<title>Biochemical parameters</title>
<p>
<xref ref-type="fig" rid="f2">
<bold>Figures&#xa0;2A, B</bold>
</xref> illustrated serum glucose and albumin levels in different treatment and control groups. As the dose and duration of administration increased, serum glucose increased significantly in the treatment groups. The higher-dosed groups (5x and 10x) showed elevated serum glucose. On day 10 post-administration, its level decreased significantly in all groups except for the 10x group. The serum albumin levels in the 1x group significantly rose over the periods of 10, 20, and 30 days, followed by a minor decrease upon discontinuation of the dosage. While in other OTC groups, serum albumin was significantly lower than in the 1x group on all days of observation (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2B</bold>
</xref>). A significant rise in AST levels in all treatment groups on day 10 was observed, which decreased with time (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3A</bold>
</xref>), The ALT levels significantly increased in all treatment groups with dose and time compared to the control (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3B</bold>
</xref>). A dose-dependent decrease in ALP activity was observed on all days compared to the control, with the maximum reduction in the 10x group even on day 10 post-administration (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3C</bold>
</xref>).</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>
<bold>(A)</bold> Glucose and <bold>(B)</bold> albumin content of <italic>H</italic>. <italic>fossilis</italic> in the control and treated groups. Error bars with different alphabets on a specific day indicated significant differences (<italic>p</italic> &lt;&#x2009;0.05) among groups. Experimental period: Day 10, 20 and 30: OTC dosing period. Day 40: Day 10 post-OTC-dosing.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fimmu-15-1478114-g002.tif"/>
</fig>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>
<bold>(A)</bold> AST, <bold>(B)</bold> ALT and <bold>(C)</bold> ALP activity of <italic>H</italic>. <italic>fossilis</italic> in the control and treated groups. Error bars with different alphabets on a specific day indicated significant differences (<italic>p</italic> &lt;&#x2009;0.05) among groups. Experimental period: Day 10, 20 and 30: OTC dosing period. Day 40: Day 10 post-OTC-dosing.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fimmu-15-1478114-g003.tif"/>
</fig>
</sec>
<sec id="s4_4">
<title>Oxidative stress biomarkers</title>
<p>The results of the oxidative stress biomarkers in the liver tissues at different time points are shown in <xref ref-type="fig" rid="f4">
<bold>Figures&#xa0;4A&#x2013;C</bold>
</xref>. A significant dose-dependent increase in SOD, CAT, and MDA levels were noted on all days except day 40 of OTC administration compared to the control. The higher dose groups exhibited the highest activity. On day 40 (post-administration), their levels decreased significantly in all groups and were comparable to the control (<xref ref-type="fig" rid="f4">
<bold>Figures&#xa0;4A&#x2013;C</bold>
</xref>).</p>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>
<bold>(A)</bold> SOD, <bold>(B)</bold> CAT and <bold>(C)</bold> MDA activity of <italic>H</italic>. <italic>fossilis</italic> in the control and treated groups. Error bars with different alphabets on a specific day indicated significant differences (<italic>p</italic> &lt;&#x2009;0.05) among groups. Experimental period: Day 10, 20 and 30: OTC dosing period. Day 40: Day 10 post-OTC-dosing.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fimmu-15-1478114-g004.tif"/>
</fig>
</sec>
<sec id="s4_5">
<title>Residues in muscle</title>
<p>The dose- and time-dependent residue accumulation and depletion in the edible tissue of the OTC-fed <italic>H. fossilis</italic> are presented in <xref ref-type="table" rid="T3">
<bold>Table&#xa0;3</bold>
</xref>. Among the treatment groups, the 10x group recorded the highest residues (423.3 &#xb1; 3.38 &#xb5;g/kg), surpassing the maximum residual limit (MRL), in the edible flesh on day 30 of administration. However, in the therapeutic dose group, the residues remained below the MRL, measuring 79.5 &#xb1; 2.43 &#xb5;g/kg on day 30 of administration. After 10 days of dose cessation, the residues were reduced below the MRL of 100 &#xb5;g/kg in 1x and 3x groups, while in other groups the levels were high (<xref ref-type="table" rid="T3">
<bold>Table&#xa0;3</bold>
</xref>).</p>
<table-wrap id="T3" position="float">
<label>Table&#xa0;3</label>
<caption>
<p>Oxytetracycline (OTC) residues in the edible muscle tissues of <italic>H. fossilis</italic> as assessed by LC-MS/MS in different treatment groups.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="top" rowspan="2" align="center">Treatment groups</th>
<th valign="top" colspan="4" align="center">OTC residue levels (&#xb5;g/kg)</th>
</tr>
<tr>
<th valign="top" align="center">10<sup>th</sup> Day</th>
<th valign="top" align="center">20<sup>th</sup> Day</th>
<th valign="top" align="center">30<sup>th</sup> Day</th>
<th valign="top" align="center">40<sup>th</sup> Day</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="center">Control (Basal diet)</td>
<td valign="top" align="center">ND</td>
<td valign="top" align="center">ND</td>
<td valign="top" align="center">ND</td>
<td valign="top" align="center">ND</td>
</tr>
<tr>
<td valign="top" align="center">T1 (80 mg/kg biomass/day)</td>
<td valign="top" align="center">19.70 &#xb1; 0.73<sup>a</sup>
</td>
<td valign="top" align="center">42.50 &#xb1; 1.33<sup>b</sup>
</td>
<td valign="top" align="center">79.50 &#xb1; 2.43<sup>c</sup>
</td>
<td valign="top" align="center">24.00 &#xb1; 0.92<sup>a</sup>
</td>
</tr>
<tr>
<td valign="top" align="center">T2 (240 mg/kg biomass/day)</td>
<td valign="top" align="center">45.40 &#xb1; 1.32<sup>a</sup>
</td>
<td valign="top" align="center">93.00 &#xb1; 2.22<sup>b</sup>
</td>
<td valign="top" align="center">238.00 &#xb1; 4.03<sup>c</sup>
</td>
<td valign="top" align="center">86.00 &#xb1; 1.04<sup>b</sup>
</td>
</tr>
<tr>
<td valign="top" align="center">T3 (400 mg/kg biomass/day)</td>
<td valign="top" align="center">78.30 &#xb1; 1.05<sup>a</sup>
</td>
<td valign="top" align="center">142.00 &#xb1; 2.03<sup>b</sup>
</td>
<td valign="top" align="center">289.30 &#xb1; 2.84<sup>c</sup>
</td>
<td valign="top" align="center">112.00 &#xb1; 2.06<sup>b</sup>
</td>
</tr>
<tr>
<td valign="top" align="center">T4 (800 mg/kg biomass/day)</td>
<td valign="top" align="center">175.00 &#xb1; 2.14<sup>a</sup>
</td>
<td valign="top" align="center">219.30 &#xb1; 2.14<sup>b</sup>
</td>
<td valign="top" align="center">423.30 &#xb1; 3.38<sup>c</sup>
</td>
<td valign="top" align="center">243.00 &#xb1; 2.43<sup>b</sup>
</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Values within a row with different superscripts (a-c) differed significantly (p&lt;&#x2009;0.05) ND, Not detected. Experimental period: Day 10, 20 and 30: OTC dosing period. Day 40: Day 10 post-OTC-dosing.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="s4_6">
<title>Liver histopathology</title>
<p>The control group exhibited healthy and normal histological features, characterized by intact sinusoidal architecture and hepatic cells with nuclei throughout the experimental trial. The liver structure was severely impacted by OTC administration at the highest dose across all time durations. It displayed significant changes such as haemorrhage congestion, nuclear pyknosis, cellular hypertrophy, and vacuolation. While in other groups, the changes were minimal (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5</bold>
</xref>).</p>
<fig id="f5" position="float">
<label>Figure&#xa0;5</label>
<caption>
<p>Histopathological changes in <italic>H</italic>. <italic>fossilis</italic> liver tissues of treated groups: Control with normal hepatocytes and sinusoidal architecture; <bold>(A)</bold> T1 treatment group with 1&#xd7; OTC in diet for 30 days showing almost normal architecture, <bold>(B)</bold> T2 treatment group with 3&#xd7; OTC for 30 days showing extensive congested hepatic sinusoids; <bold>(C)</bold> T3 treatment group with 5&#xd7; OTC showing nuclear pyknosis and haemorrhages; <bold>(D)</bold> T4 treatment group with 10&#xd7; OTC showing diffuse haemorrhage, and cellular hypertrophy; <bold>(E)</bold> T4 treatment group with 10&#xd7; OTC showing vacuolation, and haemorrhage on the 30<sup>th</sup> day (hae, haemorrhage; np, nuclear pyknosis; con, congestion; vac, vacuolation; ch,cellular hypertrophy).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fimmu-15-1478114-g005.tif"/>
</fig>
</sec>
</sec>
<sec id="s5" sec-type="discussion">
<title>Discussion</title>
<p>OTC is a widely used and highly preferred tetracycline-based antibiotic that is effective against a wide range of bacteria that can infect fish and is legal to use in aquaculture around the world (<xref ref-type="bibr" rid="B5">5</xref>, <xref ref-type="bibr" rid="B16">16</xref>, <xref ref-type="bibr" rid="B29">29</xref>). The most common method for administering antibiotics to treat and manage bacterial diseases in aquaculture is through medicated feed at a therapeutic or recommended dose (<xref ref-type="bibr" rid="B7">7</xref>, <xref ref-type="bibr" rid="B11">11</xref>, <xref ref-type="bibr" rid="B30">30</xref>). In this study, the tested bacterial strains were infective and isolated from sick fish with no documented evidence of OTC use. The range of OTC&#x2019;s MIC values (0.5-8.0 &#xb5;g/mL) against the examined pathogens was low, corroborating the findings of Gaunt et&#xa0;al. (<xref ref-type="bibr" rid="B31">31</xref>) in <italic>Aeromonas</italic> spp., <italic>Edwardsiella</italic> spp. and <italic>Streptococcus</italic> spp., with MIC values less than 1.0 regardless of their isolation location and times. These observations on low MIC can help predict the likelihood of a successful therapeutic intervention (<xref ref-type="bibr" rid="B32">32</xref>, <xref ref-type="bibr" rid="B33">33</xref>). Before approval, the antibiotics are tested for their effectiveness, biosafety, impact on the environment, and ability to leave residues in the muscle (<xref ref-type="bibr" rid="B9">9</xref>, <xref ref-type="bibr" rid="B30">30</xref>, <xref ref-type="bibr" rid="B34">34</xref>, <xref ref-type="bibr" rid="B35">35</xref>). As there are no effective guidelines on the use of OTC on tropical Indian fish, the current work assessed the safety of its oral supplementation at the therapeutic dose as well as up to ten times the therapeutic dose and its effect on several parameters of <italic>H. fossilis.</italic> Dietary supplementation did not cause any mortalities in treatment groups, thus proving its safety even at the highest dose and extended feeding regime. These results were comparable with previous studies recorded in rohu (<xref ref-type="bibr" rid="B12">12</xref>), snub-nosed pompano (<xref ref-type="bibr" rid="B13">13</xref>), Nile tilapia (<xref ref-type="bibr" rid="B14">14</xref>), striped catfish (<xref ref-type="bibr" rid="B15">15</xref>) and mrigal (<xref ref-type="bibr" rid="B16">16</xref>). However, the results revealed growth retardation in the treatment groups. Earlier reports suggested adverse impacts of OTC on fish possibly due to impaired nutritional absorption and assimilation, internal vital organ injury, disrupted metabolic functions and gastrointestinal microbiome dysbacteriosis (<xref ref-type="bibr" rid="B35">35</xref>, <xref ref-type="bibr" rid="B36">36</xref>). Also, no significant differences in growth in rohu and mrigal upon feeding graded doses of OTC for up to 30 days were documented (<xref ref-type="bibr" rid="B12">12</xref>, <xref ref-type="bibr" rid="B16">16</xref>). On the contrary, some reports categorized OTC as a growth promoter in striped catfish (<xref ref-type="bibr" rid="B15">15</xref>), Nile tilapia (<xref ref-type="bibr" rid="B37">37</xref>), and channel catfish (<xref ref-type="bibr" rid="B38">38</xref>).</p>
<p>It is reported that OTC-supplemented feed either enhances or reduces the non-specific immune responses (<xref ref-type="bibr" rid="B39">39</xref>). The diminished activities of the tested innate immune parameters like RBA, MPO, and lysozyme indicated immunosuppression, particularly at the higher OTC doses (5x-10x groups), supporting reports of Hand et&#xa0;al. (<xref ref-type="bibr" rid="B40">40</xref>). However, in agreement with the present results, the innate immunity indices of sea bream increased upon OTC administration at 75 mg/kg biomass/day for 10 days, which was retained up to three weeks after cessation of OTC dosing and then returned to normal levels (<xref ref-type="bibr" rid="B41">41</xref>) and the therapeutic dose demarcated significant enhancement in non-specific immunity parameters such as RBA and MPO. The present results on compromised immunity during the feeding trials suggest that the impact on immune responses is species-specific as the fish immunity varies with rearing conditions, fish species, antimicrobial dose, water temperature, route of delivery, and other conditions that affect drug absorption (<xref ref-type="bibr" rid="B36">36</xref>).</p>
<p>With the gradual increase in dose and duration of OTC administration, serum glucose increased, suggesting an aberrant metabolic activity and, consequently, stress-related events in fish similar to earlier studies (<xref ref-type="bibr" rid="B12">12</xref>, <xref ref-type="bibr" rid="B15">15</xref>). The albumin level increased in the lower dose groups but declined in the higher dose groups, indicating biphasic activities and altered physiological status. The current finding reported reduced AST activity after an initial hike in the treatment groups, while ALT activity increased significantly in all treatment groups. The results indicated liver injury and dysfunction (<xref ref-type="bibr" rid="B42">42</xref>, <xref ref-type="bibr" rid="B43">43</xref>), attributable to oxidative stress. Furthermore, elevated ALT levels in serum are suggestive of hepatitis arising from the toxicity of dietary OTC in <italic>H. fossilis</italic> at higher doses and the extensive burden on hepatic integrity. Concurrent with the present findings, Manna et&#xa0;al. (<xref ref-type="bibr" rid="B15">15</xref>) reported serum AST and ALT upsurge in catfish<italic>-</italic>fed graded doses (1x - 10x) of OTC. In another study, biphasic activities of AST and ALT were documented, with the highest levels in lower OTC-dosed fish than at the higher OTC-dosed fish (<xref ref-type="bibr" rid="B44">44</xref>). The increased concentration of these liver functional enzymes at lower doses and initial treatment times and then decreased concentration at higher doses and prolonged treatment may hypothesized to be the responses of <italic>H. fossilis</italic> is more likely due to terminal stages of feeding graded doses of OTC. Serum ALP was lower in fish-fed-graded OTC doses than in the control. The ALP levels decreased significantly in the 5x and 10x groups on the 30th day of administration, which indicated impaired phosphorus metabolism in OTC-fed catfish. With dose discontinuation, the levels of AST almost stabilized. On the other hand, the ALT and ALP levels were either higher or lower, indicating severe liver injury.</p>
<p>The SOD and CAT are vital for the detoxification of harmful reactive oxygen species, protecting cells, and maintaining homeostasis (<xref ref-type="bibr" rid="B45">45</xref>, <xref ref-type="bibr" rid="B46">46</xref>). The MDA levels are considered an indicator of lipid peroxidation caused by oxidative stress and induced by exposure of fish to nutrients, pollutants, antimicrobials, etc. (<xref ref-type="bibr" rid="B45">45</xref>, <xref ref-type="bibr" rid="B46">46</xref>). The present work documented a significant dose- and time-dependent increase in SOD, CAT, and MDA in comparison to control, revealing an impairment in the antioxidant systems of <italic>H. fossilis</italic> as a result of oxidative stress. Comparable results were obtained in pearl gentian grouper (<xref ref-type="bibr" rid="B10">10</xref>) and tilapia (<xref ref-type="bibr" rid="B14">14</xref>, <xref ref-type="bibr" rid="B35">35</xref>) during the oral supplementation of OTC at varied doses. These results intricated an interplay between oxidative stress and drug toxicity on the vulnerability of aquatic organisms and highlighted the importance of monitoring antioxidant defences as a crucial aspect of fish health assessment.</p>
<p>While temperate fish species have well-documented data on residues (<xref ref-type="bibr" rid="B30">30</xref>, <xref ref-type="bibr" rid="B39">39</xref>, <xref ref-type="bibr" rid="B47">47</xref>), little is known about the depletion of OTC in tropical fish species. In recent years, reports on OTC residues in tropical fish species, including rohu (<xref ref-type="bibr" rid="B12">12</xref>), striped catfish (<xref ref-type="bibr" rid="B15">15</xref>), Nile tilapia (<xref ref-type="bibr" rid="B14">14</xref>), mrigal (<xref ref-type="bibr" rid="B16">16</xref>), and snub-nosed pompano (<xref ref-type="bibr" rid="B13">13</xref>) are expanding. The data on antibiotic residues in edible muscle tissues of each fish species is critical for the preparation of food safety guidelines (<xref ref-type="bibr" rid="B13">13</xref>), and comprehensive documentation of food safety rules for medication withdrawal times in aquaculture is required. The regulatory firms have set the MRL for OTC in edible fish flesh as 200 &#xb5;g/kg (<xref ref-type="bibr" rid="B48">48</xref>) and 100 &#xb5;g/kg (<xref ref-type="bibr" rid="B49">49</xref>). In this study, the residue levels in the edible flesh of <italic>H. fossilis</italic> were found to be significantly different based on dose and duration of administration. The therapeutic dose group documented residues below the MRL, indicating their compliance with the regulatory guidelines (<xref ref-type="bibr" rid="B48">48</xref>, <xref ref-type="bibr" rid="B49">49</xref>). In contrast, OTC residues were above the MRL in higher-dosed groups. The residue accretion in various tissues led to metabolic stress, impaired liver function, oxidative stress and alterations in the liver histoarchitecture. These findings suggested that the use of a therapeutic dose of OTC even for an extended duration poses minimal threat to catfish health or human consumers.</p>
<p>The liver is the best organ for histopathological investigations to assess the drug effects (<xref ref-type="bibr" rid="B35">35</xref>, <xref ref-type="bibr" rid="B50">50</xref>), as it is imperative for fish growth and metabolism (<xref ref-type="bibr" rid="B51">51</xref>). The histoarchitecture of the liver was severely impacted by OTC dose and duration and was directly correlated with the results of oxidative stress and liver function biomarkers. The hepatic parenchyma of the higher-dosed groups showed severe congestion, haemorrhage, and vacuolation, corroborating several earlier studies that reported hepatic vacuolization upon OTC administration in varied fish species (<xref ref-type="bibr" rid="B13">13</xref>, <xref ref-type="bibr" rid="B15">15</xref>, <xref ref-type="bibr" rid="B50">50</xref>&#x2013;<xref ref-type="bibr" rid="B53">53</xref>). Vacuole formation may be a consequence of severe damage and degeneration as the liver is the main detoxification organ. It is, therefore, important to take these hepatotoxic effects into account, particularly if the fish are fed higher doses of antibiotics or longer durations.</p>
</sec>
<sec id="s6" sec-type="conclusions">
<title>Conclusion</title>
<p>In this study, OTC did not enhance fish growth, even when administered over an extended period. Notably, the therapeutic OTC dose (80 mg/kg biomass/day) did not negatively impact the non-specific immunological indices, enzymatic activities, stress biomarkers and residue accretion. However, administering OTC at higher doses (5x and 10x) had significant adverse effects on innate immunity, biochemical and oxidative stress markers, and liver histopathology. Therefore, to maintain optimal immunological and physiological indices in <italic>H. fossilis</italic>, a therapeutic dose of 80 mg/kg biomass/day may be adhered to for the treatment of bacterial infections. Additionally, higher doses led to a significant accumulation of OTC residues in the edible muscle of <italic>H. fossilis</italic>, which persisted even on day 10 of discontinuation of administration. Considering the negative effects of antibiotics, future research should focus on alternatives or other next-generation antibiotics to better control bacterial infections. This strategy will minimize the impact of antibiotics on cultured fish and other aquatic flora and fauna, as well as mitigate the issue of antimicrobial resistance and public health.</p>
</sec>
</body>
<back>
<sec id="s8" sec-type="data-availability">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/supplementary material. Further inquiries can be directed to the corresponding authors.</p>
</sec>
<sec id="s9" sec-type="ethics-statement">
<title>Ethics statement</title>
<p>The animal study was approved by Experimental trial with live aquatic animals were carried out at the wet laboratory conditions of fish health management division of ICAR-Central Institute of Freshwater Aquaculture, Bhubaneswar, India. The live fish experiments were completed in acquiescence with guidelines provided in ARRIVE (Percie du Sert et&#xa0;al., 2020) and ethical committee of ICAR- CIFA, Bhubaneswar. All the methods/procedures of All India Network Project were endorsed by Indian Council of Agricultural Research, Government of India, New Delhi (CIBA/AI-NPFH/2020-2025). Each and every procedure were as per the humanly condition to reduce any sort of troubles to live experimental animals. The study was conducted in accordance with the local legislation and institutional requirements.</p>
</sec>
<sec id="s10" sec-type="author-contributions">
<title>Author contributions</title>
<p>PC: Methodology, Writing &#x2013; original draft, Investigation, Validation, Writing &#x2013; review &amp; editing. SN: Investigation, Writing &#x2013; review &amp; editing. SRS: Investigation, Writing &#x2013; review &amp; editing. RD: Validation, Writing &#x2013; review &amp; editing. SNS: Data curation, Methodology, Writing &#x2013; review &amp; editing. SP: Data curation, Methodology, Writing &#x2013; review &amp; editing. TA: Writing &#x2013; review &amp; editing. PP: Funding acquisition, Investigation, Writing &#x2013; review &amp; editing. PS: Investigation, Supervision, Writing &#x2013; review &amp; editing. SM: Funding acquisition, Project administration, Writing &#x2013; review &amp; editing.</p>
</sec>
<sec id="s11" sec-type="funding-information">
<title>Funding</title>
<p>The author(s) declare financial support was received for the research, authorship, and/or publication of this article. The authors acknowledge the All-India Network Project on Fish Health funded by the Indian Council of Agriculture Research, Ministry of Agriculture and Farmer&#x2019;s Welfare, Government of India.</p>
</sec>
<ack>
<title>Acknowledgments</title>
<p>All the authors acknowledge the financial supports extended by Indian Council of Agriculture Research (ICAR), New Delhi, India in the form of All-India Network Project on Fish Health. Authors also duly acknowledge the guidance, and facilities extended by the Director, ICAR-CIFA, Bhubaneswar for conducting such an experiment and successful completion of the study.</p>
</ack>
<sec id="s12" sec-type="COI-statement">
<title>Conflict of interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec id="s13" sec-type="disclaimer">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
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