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<journal-id journal-id-type="publisher-id">Front. Bioeng. Biotechnol.</journal-id>
<journal-title>Frontiers in Bioengineering and Biotechnology</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Bioeng. Biotechnol.</abbrev-journal-title>
<issn pub-type="epub">2296-4185</issn>
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<publisher-name>Frontiers Media S.A.</publisher-name>
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<article-id pub-id-type="publisher-id">1603975</article-id>
<article-id pub-id-type="doi">10.3389/fbioe.2025.1603975</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Bioengineering and Biotechnology</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Adaptive responses of <italic>Gordonia alkanivorans</italic> IEGM 1277 to the action of meloxicam and its efficient biodegradation</article-title>
<alt-title alt-title-type="left-running-head">Tyan et al.</alt-title>
<alt-title alt-title-type="right-running-head">
<ext-link ext-link-type="uri" xlink:href="https://doi.org/10.3389/fbioe.2025.1603975">10.3389/fbioe.2025.1603975</ext-link>
</alt-title>
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<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Tyan</surname>
<given-names>Semyon</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="corresp" rid="c001">&#x2a;</xref>
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<contrib contrib-type="author">
<name>
<surname>Kostrikina</surname>
<given-names>Nadezhda</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
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<contrib contrib-type="author">
<name>
<surname>Sorokin</surname>
<given-names>Vladimir</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
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<contrib contrib-type="author">
<name>
<surname>Mulyukin</surname>
<given-names>Andrey</given-names>
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<xref ref-type="aff" rid="aff2">
<sup>2</sup>
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<name>
<surname>Ivshina</surname>
<given-names>Irina</given-names>
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<xref ref-type="aff" rid="aff1">
<sup>1</sup>
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<aff id="aff1">
<sup>1</sup>
<institution>Institute of Ecology and Genetics of Microorganisms</institution>, <institution>Federal Research Center</institution>, <institution>Ural Branch of The Russian Academy</institution>, <addr-line>Perm</addr-line>, <country>Russia</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Winogradsky Institute of Microbiology</institution>, <institution>Research Center of Biotechnology</institution>, <institution>Russian Academy of Sciences</institution>, <addr-line>Moscow</addr-line>, <country>Russia</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>
<bold>Edited by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/858490/overview">Zhen Fang</ext-link>, Jiangsu University, China</p>
</fn>
<fn fn-type="edited-by">
<p>
<bold>Reviewed by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3053585/overview">Alicia Jeannette Baumann</ext-link>, National University of Misiones, Argentina</p>
<p>
<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3099959/overview">Yaoli Wei</ext-link>, Taiyuan Institute of Technology, China</p>
</fn>
<corresp id="c001">&#x2a;Correspondence: Semyon Tyan, <email>vviolent00@mail.ru</email>; Irina Ivshina, <email>ivshina@iegm.ru</email>
</corresp>
</author-notes>
<pub-date pub-type="epub">
<day>23</day>
<month>07</month>
<year>2025</year>
</pub-date>
<pub-date pub-type="collection">
<year>2025</year>
</pub-date>
<volume>13</volume>
<elocation-id>1603975</elocation-id>
<history>
<date date-type="received">
<day>01</day>
<month>04</month>
<year>2025</year>
</date>
<date date-type="accepted">
<day>04</day>
<month>07</month>
<year>2025</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2025 Tyan, Kostrikina, Sorokin, Mulyukin and Ivshina.</copyright-statement>
<copyright-year>2025</copyright-year>
<copyright-holder>Tyan, Kostrikina, Sorokin, Mulyukin and Ivshina</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>Introduction</title>
<p>Pharmaceutical contaminants such as meloxicam pose significant environmental risks due to their persistence and toxicity. The biodegradation potential of actinomycetes, particularly representatives of <italic>Gordonia</italic>, offers promising avenues for eco-friendly wastewater treatment. However, the ability of <italic>Gordonia</italic> to fully degrade meloxicam has not been previously demonstrated.</p>
</sec>
<sec>
<title>Methods</title>
<p>The biodegradation of meloxicam was investigated using <italic>G. alkanivorans</italic> IEGM 1277 as a model organism. Metabolite identification was performed using liquid chromatography-mass spectrometry (LC-MS). Candidate genes encoding meloxicam-oxidising enzymes were identified via genomic analysis. Adaptive bacterial responses to meloxicam exposure were characterised using atomic force microscopy (AFM), transmission electron microscopy (TEM), and energy-dispersive X-ray spectroscopy (EDX).</p>
</sec>
<sec>
<title>Results</title>
<p>
<italic>G. alkanivorans</italic> IEGM 1277 successfully decomposed meloxicam into primary metabolites, 5&#x27;-hydroxymethyl- and 5&#x27;-carboxymeloxicam, which exhibited reduced (eco)toxicity compared to the parent compound. Genomic analysis revealed several candidate genes potentially involved in meloxicam oxidation. Microscopic and spectroscopic analyses demonstrated significant phenotypic and metabolic changes in bacterial cells, indicating adaptive defence mechanisms triggered by meloxicam exposure.</p>
</sec>
<sec>
<title>Discussion</title>
<p>This study provides the first evidence of complete meloxicam biodegradation by <italic>Gordonia</italic> and elucidates the underlying enzymatic and adaptive cellular responses. The findings highlight the potential application of <italic>G. alkanivorans</italic> IEGM 1277 in developing efficient and environmentally safe biotechnologies for pharmaceutical wastewater treatment.</p>
</sec>
</abstract>
<kwd-group>
<kwd>non-steroidal anti-inflammatory drugs (NSAIDs)</kwd>
<kwd>meloxicam</kwd>
<kwd>pharmaceutical pollution</kwd>
<kwd>
<italic>Gordonia</italic>
</kwd>
<kwd>biodegradation</kwd>
<kwd>bacterial cell responses</kwd>
</kwd-group>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Bioprocess Engineering</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1">
<title>1 Introduction</title>
<p>The contamination of the environment with pharmaceuticals and its resultant harm constitutes a significant worldwide issue of indisputable relevance (<xref ref-type="bibr" rid="B4">Boxall and Brooks, 2024</xref>; <xref ref-type="bibr" rid="B15">Gupta et al., 2024</xref>; <xref ref-type="bibr" rid="B56">Wilkinson et al., 2024</xref>). Once released, these compounds act as hazardous pollutants, driving extreme conditions and ecotoxic effects (<xref ref-type="bibr" rid="B52">Wang et al., 2024</xref>; <xref ref-type="bibr" rid="B28">Meena et al., 2025</xref>). Even at environmentally relevant concentrations, residual pharmaceuticals and their transformation products exert acute and chronic adverse impacts on terrestrial and aquatic organisms (<xref ref-type="bibr" rid="B5">Carter et al., 2024</xref>; <xref ref-type="bibr" rid="B39">Saeed et al., 2024</xref>). The effects of pharmpollutants on many organism groups, particularly microorganisms &#x2013; primary responders to xenobiotic &#x2013; remain insufficiently studied, and their adaptive mechanisms are largely unexplored (<xref ref-type="bibr" rid="B48">&#x15a;wiacka et al., 2021</xref>). Non-steroidal anti-inflammatory drugs (NSAIDs), such as diclofenac, ibuprofen, ketoprofen, and naproxen, are the most frequently reported and toxic pharmaceutical pollutants (<xref ref-type="bibr" rid="B17">Huynh et al., 2023</xref>). Meloxicam (MLX), a widely used NSAID, has been reported to occur in natural ecosystems and living organisms and is thus considered a persistent pharmaceutical pollutant (<xref ref-type="bibr" rid="B65">Zorrilla et al., 2015</xref>; <xref ref-type="bibr" rid="B16">Herrero-Villar et al., 2020</xref>; <xref ref-type="bibr" rid="B53">Wang et al., 2021</xref>). Nevertheless, there are significant knowledge gaps concerning its environmental fate (<xref ref-type="bibr" rid="B56">Wilkinson et al., 2024</xref>). As demonstrated by a paucity of studies, the MLX concentrations in different aquatic systems may vary significantly, from nano- to micrograms per 1&#xa0;L (<xref ref-type="bibr" rid="B13">Gros et al., 2012</xref>; <xref ref-type="bibr" rid="B21">Jim&#xe9;nez et al., 2018</xref>), although the data on its occurrence in environmental samples for many geographic regions, including Russia, are still absent.</p>
<p>It is important to note that there is a risk of environmental contamination associated with MLX, which can be attributed to its extensive consumption and large-scale production (<xref ref-type="bibr" rid="B1">Ahmed et al., 2005</xref>; <xref ref-type="bibr" rid="B3">Bekker et al., 2018</xref>). Its main pharmacological action mechanism is associated with the selective blockade of cyclooxygenase-2, which is formed at sites of tissue damage and is responsible for the active synthesis of prostaglandins (<xref ref-type="bibr" rid="B50">Tavares, 2000</xref>). Approximately 20 million prescriptions for MLX were issued in the US in 2011, with an annual average of 9 million (<xref ref-type="bibr" rid="B8">Dalal et al., 2017</xref>; <xref ref-type="bibr" rid="B25">LiverTox, 2025</xref>). MLX is manufactured in India, Germany, the Republic of Belarus, the Russian Federation, and other countries with a broad distribution network across the global market. In Russia, 63.7 million packs of MLX have been sold over the past 25&#xa0;years (<xref ref-type="bibr" rid="B22">Karateev et al., 2021</xref>).</p>
<p>Meloxicam (MLX, CAS&#x23; 71125-38-7; C<sub>14</sub>H<sub>13</sub>N<sub>3</sub>O<sub>4</sub>S<sub>2</sub>, 4-hydroxy-2-methyl-N-(5-methyl-2-thiazolyl)-2<italic>H</italic>-1,2-benzothiazine-3-carboxamide 1,1-dioxide, also known as Mobic<sup>&#xae;</sup>) is a highly toxic oxicam-class NSAID. The detrimental effects of MLX on invertebrate animals, fish, birds, and mammals have been well-documented. MLX has been demonstrated to cause neuronal damage in the roundworm <italic>Caenorhabditis elegans</italic> (<xref ref-type="bibr" rid="B9">da Silva et al., 2020</xref>); to cause oxidative stress in the common carp <italic>Cyprinus carpio</italic> (<xref ref-type="bibr" rid="B44">Sheikhlangi et al., 2023</xref>); and to result in DNA damage in mice (<xref ref-type="bibr" rid="B10">da Silva et al., 2022</xref>). However, a significant proportion of groups of organisms have not yet been studied in relation to the effects of MLX.</p>
<p>Pharmaceutical compounds persist in aquatic and terrestrial ecosystems due to ineffective removal by conventional physicochemical wastewater treatments (<xref ref-type="bibr" rid="B4">Boxall and Brooks, 2024</xref>; <xref ref-type="bibr" rid="B56">Wilkinson et al., 2024</xref>). Consequently, alternative remediation strategies are required. Biodegradation, leveraging microbial enzymatic activity for pharmaceutical decomposition, represents the most promising approach (<xref ref-type="bibr" rid="B30">Mishra et al., 2021</xref>; <xref ref-type="bibr" rid="B7">Crowther et al., 2024</xref>; <xref ref-type="bibr" rid="B42">Shah et al., 2024</xref>). This method supports eco-friendly wastewater management and aligns with Sustainable Development Goals by minimising environmental impact (<xref ref-type="bibr" rid="B45">Singh et al., 2024</xref>).</p>
<p>It is a conceivable, albeit as yet unexamined, hypothesis that the representatives of <italic>Actinomycetes</italic> have the capacity to destroy MLX. Genus <italic>Rhodococcus</italic> exhibit remarkable metabolic versatility and genomic plasticity, enabling their survival in diverse natural and anthropogenically polluted environments. <italic>Rhodococcus</italic> species, recognised for their extensive capacity to degrade xenobiotics such as drotaverine (<xref ref-type="bibr" rid="B18">Ivshina et al., 2015</xref>), diclofenac (<xref ref-type="bibr" rid="B20">Ivshina et al., 2019</xref>), and ibuprofen (<xref ref-type="bibr" rid="B19">Ivshina et al., 2021</xref>) &#x2013; pharmaceuticals frequently detected in aquatic ecosystems and identified by the European Commission as posing significant environmental risks (<xref ref-type="bibr" rid="B64">Zhou et al., 2019</xref>) &#x2013; play a critical role in bioremediating contaminated ecosystems. The other related actinomycetes <italic>Gordonia sensu stricto</italic> demonstrates robust adaptability to changing climatic and ecological conditions, with metabolic capabilities that facilitate the degradation of complex organic xenobiotics, including heterocyclic compounds, aromatic hydrocarbons, and polyethylene (<xref ref-type="bibr" rid="B47">Sowani et al., 2017</xref>; <xref ref-type="bibr" rid="B41">S&#xe1;nchez-Su&#xe1;rez et al., 2022</xref>; <xref ref-type="bibr" rid="B11">Frantsuzova et al., 2023</xref>). It is hypothesised that <italic>Gordonia</italic> multifunctional oxygenase systems would catalyse direct MLX oxidation processes, including the introduction of hydroxyl groups into the molecule&#x2019;s aromatic ring up to complete decomposition of its chemical structure. However, an issue with the tolerance of different actinobacterial species to MLX remains unresolved.</p>
<p>The objectives of this study were to characterise the response of <italic>Gordonia</italic> strains to MLX, identify the most efficient MLX-degrading strains, and elucidate the underlying degradation mechanisms.</p>
</sec>
<sec sec-type="materials|methods" id="s2">
<title>2 Materials and methods</title>
<sec id="s2-1">
<title>2.1 Bacterial strains and chemicals</title>
<p>In the study, 20 strains of actinomycetes belonging to different <italic>Gordonia</italic> species were used &#x2013; <italic>G. alkanivorans</italic> (3 strains), <italic>G. amarae</italic> (1 strain), <italic>G. amicalis</italic> (1 strain), <italic>G. rubripertincta</italic> (14 strains), <italic>G. sputi</italic> (1 strain) from the Regional Specialised Collection of Alkanotrophic Microorganisms (acronym IEGM, the World Federation for Culture Collections &#x23; 285, <ext-link ext-link-type="uri" xlink:href="http://www.iegmcol.ru">http://www.iegmcol.ru</ext-link>) (<xref ref-type="bibr" rid="B6">Catalogue of Strains, 2025</xref>). The selection of bacterial strains was guided by distinctive ecological traits indicative of adaptation to particular environmental niches. We focused on microorganisms from areas affected by human activities to explore how they can help clean up pollution and understand how they cope with stress. This targeted approach not only augments the applied relevance of the study but also contributes to a deeper understanding of the functional diversity and ecological roles of microorganisms within contaminated ecosystems.</p>
<p>Chemical reagents, such as acetonitrile, orthophosphoric acid and <italic>n</italic>-hexadecane, were of chemically and analytically pure grade (Cryochrome, Russia; Merck, Germany; Sigma-Aldrich, United States). A Millipore Simplicity Personal Ultrapure Water System (Millipore, United States) was used to obtain the ultrapure water. MLX was used as a pure pharmaceutical substance (a light yellow powder, poorly soluble in water, odorless, with a purity of 99.99%, BLD Pharmatech Ltd., China).</p>
</sec>
<sec id="s2-2">
<title>2.2 Cultivation conditions</title>
<p>Bacterial cells were cultured in LB broth (Sigma, United States) with 160&#xa0;rpm shaking at 28&#xb0;C for 2&#xa0;days. After centrifuging the broth cultures for 15&#xa0;min at 4,500&#xa0;rpm, they were twice washed in 10&#xa0;mM phosphate buffer (pH 7.0). Bacterial cells were added to the culture medium to a final concentration of 5 &#xd7; 10<sup>8</sup>&#xa0;cells/mL. The concentration of bacterial cells was determined using spectrophotometer Lambda EZ201 (Perkin-Elmer, United States) at a wavelength of 600&#xa0;nm (OD<sub>600</sub>).</p>
</sec>
<sec id="s2-3">
<title>2.3 Minimum inhibitory concentrations of MLX</title>
<p>The minimum inhibitory concentrations (MICs) of MLX for actinomycetes was determined using the twofold dilution method in LB broth with 96-well microplates. Initial concentration selection was based on the need to overcome bacterial defences (for instance, decreased cell envelope permeability, active efflux, and enzymatic inactivation of toxicants) and identify potential antimicrobial effects of MLX that were unrelated to anti-inflammatory activity. In this regard, a working dose close to the therapeutic dose (5&#xa0;g/L) was selected. MLX was introduced at an initial concentration of 5&#xa0;g/L, followed by a twofold dilution to a final concentration of 0.15625&#xa0;g/L. 10&#xa0;&#x3bc;L of bacterial suspension was added to the resulting mixture. Incubation was performed at 28&#xb0;C for 3&#xa0;days with agitation on a Titramax 1,000 plate shaker (Heidolph, Germany). At the end of the incubation, the culture medium was stained with 50&#xa0;&#xb5;L of a 0.2% iodonitrotetrazolium chloride (INT, Sigma-Aldrich, United States) for a duration of 2&#xa0;h, thus enabling the INT reduction to insoluble red-violet INT-formazan in the presence of actively respiring cells. The formazan concentration was measured spectrophotometrically at 630&#xa0;nm sing a microplate reader (Multiskan Ascent, Thermo, Vantaa, Finland) to assess cell viability. OD<sub>630</sub> serves as an indicator of microbial vitality and bacterial cell resistance (<xref ref-type="bibr" rid="B23">Lan et al., 2019</xref>).</p>
</sec>
<sec id="s2-4">
<title>2.4 Biodegradation of MLX</title>
<p>The mineral medium RS (100&#xa0;mL in 250-mL Erlenmeyer flasks), used in biodegradation experiments, contained (g/L): K<sub>2</sub>HPO<sub>4</sub>&#x2013;2.0; KH<sub>2</sub>PO<sub>4</sub>&#x2013;2.0; KNO<sub>3</sub>&#x2013;1.0; (NH<sub>4</sub>)<sub>2</sub>SO<sub>4</sub>&#x2013;2.0; NaCl&#x2013;1.0; MgSO<sub>4</sub>&#x2013;0.2; CaCl<sub>2</sub>&#x2013;0.02, FeCl<sub>3</sub> &#xd7; 7H<sub>2</sub>O&#x2013;0.001. The stock concentrated MLX solution (with 3 &#xd7; 10<sup>&#x2212;5</sup>&#xa0;M NaOH to increase the solubility of MLX) was sterilised by passing through a nylon filter with 0.22&#xa0;&#xb5;m pore size (LabFil, China) and added to the RS medium to a final MLX concentration of 0.001% (10&#xa0;mg/L). The incubation was carried out at a temperature of 28&#xb0;C with constant stirring 160&#xa0;rpm. Light-shielded flasks were used to prevent photodegradation and photo-initiated oxidation of MLX. Since MLX cannot serve as the sole carbon and energy source for <italic>Gordonia</italic>, biodegradation was performed with 0.1% (<italic>v/v</italic>) <italic>n</italic>-hexadecane as a co-substrate, providing an accessible carbon and energy source for hydrocarbon-degrading bacteria (<xref ref-type="bibr" rid="B2">Alotaibi et al., 2022</xref>). The selected concentration is based on previous data showing that increasing <italic>n</italic>-hexadecane concentration excessively stimulates bacterial growth, whereas decreasing it insufficiently activates metabolic processes (<xref ref-type="bibr" rid="B31">Mishra and Singh, 2012</xref>). The controls were: (1) sterile drug solution in RS medium containing <italic>n</italic>-hexadecane (to assess the abiotic MLX degradation); (2) sterile drug solution in RS medium with inactivated <italic>Gordonia</italic> cells (to assess the extent of drug adsorption on bacterial cells), where the bacterial cells were inactivated upon autoclaving at 1.0&#xa0;atm three times for 20&#xa0;min; (3) RS medium containing <italic>n</italic>-hexadecane with live cells (to assess its effect on bacterial cells and to distinguish the metabolites resulting from MLX degradation).</p>
<p>In separate experiments, selective inhibition of cytochrome P450-associated monooxygenases was carried out using specific blockers (1-aminobenzotriazole, metyrapone, 4-(methylthio) phenylacetic acid) at concentrations ranging from 0.1 to 1.0&#xa0;mM to evaluate the impact of CYP450-mediated oxygenase reactions on the degradation process of MLX.</p>
</sec>
<sec id="s2-5">
<title>2.5 Analytical methods</title>
<p>The quantitative content of MLX in the culture medium was determined using high-performance liquid chromatography (HPLC) on a LC Prominence 20A chromatography column (Shimadzu, Japan) with Discovery<sup>&#xae;</sup> C18 reversed-phase sorbent (25 &#xd7; 4.6&#xa0;mm, 5&#xa0;&#x3bc;m, Supelco, United States) and diode-matrix detector (SPD-M20A). The mobile phase was phosphate buffer (pH 3.5)&#x2013;acetonitrile in a 60:40 (<italic>v/v</italic>) ratio. The eluent flow rate was 0.5&#xa0;mL/min, the column temperature was 30&#xb0;C, and the detection wavelength was 254&#xa0;nm.</p>
<p>Products of MLX decomposition were identified by liquid chromatography-mass spectrometry (LC-MS) using a LC Prominence instrument (Shimadzu, Japan) and a Luna 3uC18(2) 100A chromatographic column (150 &#xd7; 3.0&#xa0;mm) (Phenomenex, United States) with the isocratic elution. The mobile phase was composed of formic acid solution (0.1%)&#x2013;acetonitrile in an 80:20 (<italic>v/v</italic>) ratio. The eluent flow rate was 0.3&#xa0;mL/min. Detection in positive ion registration mode was by scanning in the range of <italic>m/z</italic> 50&#x2013;500. Mass spectrometric detector interface was DUIS. Flow rates of spray gas, heating gas and drying gas were 3, 10 and 10&#xa0;mL/min, respectively. Temperatures of the interface, desolvation line and heating unit were 200&#xb0;C, 300&#xb0;C and 400&#xb0;C, respectively. Flow rate of drying gas was 10&#xa0;L/min. Capillary voltage was 4000&#xa0;V. Polarity of the ionisation source was positive.</p>
</sec>
<sec id="s2-6">
<title>2.6 Respiration assay</title>
<p>The respiratory activity of the cells was measured using a 10-channel respirometer Micro-Oxymax<sup>&#xae;</sup> (Columbus Instruments, United States). Tests were performed in 300-mL Micro-Oxymax glass vials under constant stirring (160&#xa0;rpm, 28&#xb0;C &#xb1; 2&#xb0;C). The rate (&#x3bc;L/h) of &#x41e;<sub>2</sub> consumption was estimated. Automatic registration of respiratory activity parameters was conducted every 30&#xa0;min for 14&#xa0;days.</p>
</sec>
<sec id="s2-7">
<title>2.7 Microscopy</title>
<sec id="s2-7-1">
<title>2.7.1 Visualisation of lipid drops</title>
<p>Samples from the control and MLX-treated cultures were stained with Nile Red (Nanjing Dulai Biotechnology Co., Nanjing, China) and examined under an Axio Imager M2 microscope (Carl Zeiss Microscopy GmbH, Jena, Germany) according to the procedures and protocols described in (<xref ref-type="bibr" rid="B32">Mrunalini and Girisha, 2017</xref>).</p>
</sec>
<sec id="s2-7-2">
<title>2.7.2 Surface topography and nanostructure of bacterial cells</title>
<p>The influence of MLX on the cell surface morphology and topography was investigated using an Asylum MFP-3D-BIO&#x2122; atomic force microscope (AFM, Asylum Research Inc., United States). AFM-scanning was in the tapping mode in air using an AC240TS silicon cantilever (50&#x2013;90&#xa0;kHz; 0.5&#x2013;4.4&#xa0;N/m). The root means square average roughness of the cell surface, the length and width, and the volume and surface area of the cells were calculated. The images were processed using the programme Igor Pro 6.22A. (WaveMetrics, United States).</p>
</sec>
<sec id="s2-7-3">
<title>2.7.3 Transmission electron microscopy</title>
<p>Cells were harvested from the control and test cultures and fixed in 2.5% (w/v) in 0.1&#xa0;M sodium cacodylate buffer (pH 7.2) for 2.5&#xa0;h and post-fixed in 1% (w/v) osmium tetroxide in the same buffer. The fixed material was dehydrated through series of ethanol solutions to absolute ethanol saturated with uranyl acetate, and embedded in araldite. Thin sections were prepared on an ultratome (LKB, Sweden) and stained with lead citrate. Ultrathin sections were examined using a transmission electron microscope JEM-1400 (JEOL, Japan).</p>
</sec>
</sec>
<sec id="s2-8">
<title>2.8 Energy dispersive X-ray spectroscopy</title>
<p>Suspensions of harvested cells in sterile water (without treatments with fixatives) were applied onto Formvar-coated and carbon-reinforced copper grids and air-dried. TEM with energy dispersive X-ray spectroscopy (EDX) with elemental mapping were performed using a JEM-1400 microscope (JEOL, Japan) equipped with energy dispersive X-ray analysis system (EDXA, Inca Energy-350, Oxford Instruments, United Kingdom), operating at accelerating voltage of 80&#xa0;kV (tilt angle, 15&#xb0;). The elemental maps were obtained by using AZtec software (Oxford Instruments, United Kingdom).</p>
</sec>
<sec id="s2-9">
<title>2.9 Zeta-potential of bacteria</title>
<p>The electrokinetic (zeta, or &#x3b6;-) potential was measured using a ZetaSizer Nano ZS analyzer (Malvern Instruments, United Kingdom) with Malvern ZetaSizer software, v. 2.2, and calculated based on the following equation:<disp-formula id="equ1">
<mml:math id="m1">
<mml:mrow>
<mml:mi mathvariant="bold-italic">&#x3b6;</mml:mi>
<mml:mo>&#x3d;</mml:mo>
<mml:mfrac>
<mml:mrow>
<mml:mi mathvariant="bold">&#x3b7;</mml:mi>
<mml:mi mathvariant="bold">u</mml:mi>
</mml:mrow>
<mml:mrow>
<mml:msub>
<mml:mi mathvariant="bold">&#x3b5;</mml:mi>
<mml:mi mathvariant="bold">r</mml:mi>
</mml:msub>
<mml:msub>
<mml:mi mathvariant="bold">&#x3b5;</mml:mi>
<mml:mn mathvariant="bold">0</mml:mn>
</mml:msub>
</mml:mrow>
</mml:mfrac>
</mml:mrow>
</mml:math>
</disp-formula>where &#x3b6; &#x2013; zeta-potential, V; u &#x2013; electrophoretic mobility, m<sup>2</sup>/Vs; &#x3b7; &#x2013; viscosity, N/m<sup>2</sup>s; &#x3b5;<sub>0</sub> &#x2013; dielectric permittivity in vacuum, F/m; &#x3b5;<sub>r</sub> &#x2013; relative dielectric permittivity.</p>
<p>Before measurements, cells were washed twice with KNO<sub>3</sub> buffer with pelleting of biomass using HERMLE Z200A (Hermle, Germany) centrifuge and re-suspended in the same buffer to OD<sub>600</sub> 0.5 measured in a spectrophotometer Lambda EZ201 (Perkin-Elmer, United States).</p>
</sec>
<sec id="s2-10">
<title>2.10 Genomics</title>
<p>Whole-genome sequences of <italic>G. alkanivorans</italic> IEGM 1277 were obtained upon Next Generation Sequencing using a NovaSeq (Illumina, United States) sequencer.</p>
</sec>
<sec id="s2-11">
<title>2.11 <italic>In silico</italic> analysis of MLX decomposition products</title>
<p>The ecotoxicity of MLX and its bacterial degradation products was calculated using the ECOSAR (Ecological Structure Activity Relationships, <ext-link ext-link-type="uri" xlink:href="https://www.epa.gov/">https://www.epa.gov/</ext-link>) programme available in the software package EPI Suite TM (Estimation Programs Interface, EPA, United States). The ecotoxicity results were predicted based on the existing database on the toxic effects of organic compounds from various chemical classes.</p>
</sec>
<sec id="s2-12">
<title>2.12 Biological activity of MLX decomposition products</title>
<p>The biological activity profile of individual MLX metabolites was predicted using PASS (Prediction of Activity Spectra of Substances) online programme based on their structural formulas; the highest probability of bioactivity detection was taken as 1.0.</p>
</sec>
<sec id="s2-13">
<title>2.13 Biological potential of MLX decomposition products</title>
<p>The MICs of MLX degradation products against bacterial test cultures <italic>Bacillus subtilis</italic> &#x410;&#x422;&#x421;&#x421; 6633, <italic>Micrococcus luteus</italic> NCIMB 196, <italic>Staphylococcus aureus</italic> &#x410;&#x422;&#x421;&#x421; 25923, <italic>Pseudomonas plecoglossicida</italic> IEGM 2044 were assayed using the twofold serial dilutions method (<xref ref-type="bibr" rid="B55">Wiegand et al., 2008</xref>) in 96-well microplates incubated at 28&#xb0;C (for <italic>M</italic>. <italic>luteus</italic> NCIMB 196, <italic>P. plecoglossicida</italic> IEGM 2044) or 37&#xb0;C (<italic>B. subtilis</italic> &#x410;&#x422;&#x421;&#x421; 6633, <italic>S. aureus</italic> &#x410;&#x422;&#x421;&#x421; 25923) for 24&#xa0;h. Cell viability was determined upon measuring the OD of formazan at 490&#xa0;nm using a Multiskan Ascent plate spectrophotometer (Thermo Electron Corporaton, United States).</p>
</sec>
<sec id="s2-14">
<title>2.14 Statistical analysis</title>
<p>The validity of the experimental data was confirmed by control with the use of standard samples. The experiments were conducted in triplicate. Data analysis was conducted using Excel 2021 (Microsoft Inc., 2021), calculating the mean and standard deviation.</p>
</sec>
</sec>
<sec sec-type="results" id="s3">
<title>3 Results</title>
<sec id="s3-1">
<title>3.1 Resistance of <italic>Gordonia</italic> strains to MLX</title>
<p>The MIC of the MLX against the representatives of <italic>Gordonia</italic> species under study varied in the concentration range from 0.625 to 5.000 and above g/L (<xref ref-type="table" rid="T1">Table 1</xref>). The most resistant to high (MIC &#x2265;5.000&#xa0;g/L) MLX concentrations were 5 strains belonging to <italic>G</italic>. <italic>alkanivorans</italic> IEGM 1277, IEGM 1398, <italic>G</italic>. <italic>amarae</italic> IEGM 720<sup>T</sup>, <italic>G</italic>. <italic>rubripertincta</italic> IEGM 101, and IEGM 113, predominantly isolated from oil-contaminated soils, using <italic>n</italic>-hexadecane, crude oil as the only carbon source (<xref ref-type="bibr" rid="B6">Catalogue of Strains, 2025</xref>). The high resistance of the identified strains to MLX exposure determines their potential use in the removal of this drug.</p>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>MICs of the non-steroidal analgesic MLX against actinomycetes.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">MLX concentration, g/L</th>
<th align="center">Species</th>
<th align="center">Strain</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td rowspan="3" align="left">&#x3e;5</td>
<td align="center">
<italic>G</italic>. <italic>alkanivorans</italic>
</td>
<td align="center">IEGM 1277, IEGM 1398</td>
</tr>
<tr>
<td align="center">
<italic>G</italic>. <italic>amarae</italic>
</td>
<td align="center">IEGM 720<sup>T</sup>
</td>
</tr>
<tr>
<td align="center">
<italic>G</italic>. <italic>rubripertincta</italic>
</td>
<td align="center">IEGM 101, IEGM 113</td>
</tr>
<tr>
<td align="left">5</td>
<td align="center">
<italic>G</italic>. <italic>rubripertincta</italic>
</td>
<td align="center">IEGM 733, IEGM 747, IEGM 749</td>
</tr>
<tr>
<td rowspan="4" align="left">2.5</td>
<td align="center">
<italic>G</italic>. <italic>alkanivorans</italic>
</td>
<td align="center">IEGM 1385</td>
</tr>
<tr>
<td align="center">
<italic>G</italic>. <italic>amicalis</italic>
</td>
<td align="center">IEGM 1266</td>
</tr>
<tr>
<td align="center">
<italic>G</italic>. <italic>rubripertincta</italic>
</td>
<td align="center">IEGM 102, IEGM 127, IEGM 1388</td>
</tr>
<tr>
<td align="center">
<italic>G</italic>. <italic>sputi</italic>
</td>
<td align="center">IEGM 674<sup>T</sup>
</td>
</tr>
<tr>
<td align="left">1.25</td>
<td align="center">
<italic>G</italic>. <italic>rubripertincta</italic>
</td>
<td align="center">IEGM 96, IEGM 99, IEGM 106, IEGM 137, IEGM 1390</td>
</tr>
<tr>
<td align="left">0.625</td>
<td align="center">
<italic>G</italic>. <italic>rubripertincta</italic>
</td>
<td align="center">IEGM 1392</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3-2">
<title>3.2 MLX biodegradation by <italic>Gordonia alkanivorans</italic> IEGM 1277 cells and the predicted toxicity of the produced metabolites</title>
<p>As was shown in preliminary experiments, significant biodegradation MLX was not the case for the concentrations from 20 to 50&#xa0;mg/L. For further studies, we used the working MLX concentration of 10&#xa0;mg/L to simulate environmentally relevant, near-peak loading conditions for studying biodegradation and cellular responses. Although this concentration exceeds typical wastewater levels, pharmaceutical pollutants can reach elevated concentrations near discharge sources (<xref ref-type="bibr" rid="B13">Gros et al., 2012</xref>; <xref ref-type="bibr" rid="B21">Jim&#xe9;nez et al., 2018</xref>; <xref ref-type="bibr" rid="B56">Wilkinson et al., 2024</xref>). Among the studied strains (<xref ref-type="table" rid="T2">Table 2</xref>), <italic>G. alkanivorans</italic> IEGM 1277 displayed the best degradative activity with respect to MLX judging from the complete exhaustion of MLX and served as the model object for subsequent experiments. The stable and rapid decline of the MLX level started after 7&#xa0;days in cultures with <italic>G. alkanivorans</italic> IEGM 1277 with its half-disappearance by day 10 towards zero levels by the end of the experiments (<xref ref-type="fig" rid="F1">Figure 1</xref>). Chromatographic analysis (<xref ref-type="fig" rid="F2">Figure 2A</xref>) of the post-culture medium revealed compounds with <italic>m</italic>/<italic>z</italic> 368 (<xref ref-type="fig" rid="F2">Figure 2C</xref>) and 382 (<xref ref-type="fig" rid="F2">Figure 2D</xref>), corresponding to protonated metabolites of MLX: 5&#x27;-hydroxymethyl- and 5&#x27;-carboxymeloxicam. This indicates that MLX decomposition commences with a hydroxylation reaction, followed by oxidation of the side chain to a carboxylic acid (<xref ref-type="fig" rid="F3">Figure 3</xref>).</p>
<table-wrap id="T2" position="float">
<label>TABLE 2</label>
<caption>
<p>MLX content at 7 and 14&#xa0;days.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="center">Strain</th>
<th colspan="2" align="center">MLX content, %</th>
</tr>
<tr>
<th align="center">7&#xa0;days</th>
<th align="center">14&#xa0;days</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">
<italic>G</italic>. <italic>alkanivorans</italic> IEGM 1277</td>
<td align="center">19.41</td>
<td align="center">0.00</td>
</tr>
<tr>
<td align="left">
<italic>G</italic>. <italic>alkanivorans</italic> IEGM 1398</td>
<td align="center">89.57</td>
<td align="center">74.74</td>
</tr>
<tr>
<td align="left">
<italic>G</italic>. <italic>rubripertincta</italic> IEGM 733</td>
<td align="center">64.17</td>
<td align="center">70.46</td>
</tr>
</tbody>
</table>
</table-wrap>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>MLX depletion in the cultivation medium of <italic>Gordonia alkanivorans</italic> IEGM 1277.</p>
</caption>
<graphic xlink:href="fbioe-13-1603975-g001.tif">
<alt-text content-type="machine-generated">Bar and line graph showing MLX concentration over 14 days. The orange bars represent IEGM 1277 cells with MLX, decreasing to 0%. The green line with squares, representing MLX, remains at 100% throughout.</alt-text>
</graphic>
</fig>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption>
<p>Chromatogram <bold>(A)</bold> and mass spectra <bold>(B&#x2013;D)</bold> of MLX and its biodegradation products using <italic>Gordonia alkanivorans</italic> IEGM 1277. M1 &#x2013; 5&#x27;-hydroxymethylmeloxicam; M2 &#x2013; 5&#x27;-carboxymeloxicam.</p>
</caption>
<graphic xlink:href="fbioe-13-1603975-g002.tif">
<alt-text content-type="machine-generated">Chromatogram and mass spectra of a compound and its metabolites. Panel A shows an HPLC chromatogram with peaks labeled M1, M2, and MLX at different retention times. Panels B, C, and D display mass spectra for MLX, M1, and M2, respectively, illustrating molecular structures and corresponding m/z values with prominent peaks.</alt-text>
</graphic>
</fig>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption>
<p>Metabolic decomposition of MLX using <italic>Gordonia alkanivorans</italic> IEGM 1277.</p>
</caption>
<graphic xlink:href="fbioe-13-1603975-g003.tif">
<alt-text content-type="machine-generated">Biodegradation of meloxicam through two steps. First, meloxicam undergoes hydroxylation at the thiazole ring's methyl group, forming 5'-hydroxymethylmeloxicam. Then, 5'-hydroxymethylmeloxicam is oxidised to 5'-carboxylmeloxicam.</alt-text>
</graphic>
</fig>
<p>According to <italic>in silico</italic> analysis, MLX is a compound with long-term concern for aquatic organisms, whereas the products of its bacterial conversion have less pronounced toxicity. As demonstrated by the predictive analysis, the toxicity indices of MLX metabolites were found to be 1.48&#x2013;10.28 times less than those of MLX (<xref ref-type="table" rid="T3">Table 3</xref>). Our assays showed no significant antimicrobial activity of MLX metabolites against <italic>B</italic>. <italic>subtilis</italic> ATCC 6633, <italic>M</italic>. <italic>luteus</italic> NCIMB 196, <italic>S</italic>. <italic>aureus</italic> ATCC 25923, and <italic>P</italic>. <italic>plecoglossicida</italic> IEGM 2044: the MICs values exceeded 1.0&#xa0;g/L. The prediction of pharmacological potential with the PASS online programme showed a low probability of detecting significant pharmacological effects. The probability score was 0.3 with a threshold reliability value of 0.7, indicating minimal biological activity of these compounds. MLX derivatives are probably not suitable for &#x201c;green&#x201d; chemistry due to the lack of antimicrobial activity.</p>
<table-wrap id="T3" position="float">
<label>TABLE 3</label>
<caption>
<p>Predicted (eco)toxicity of MLX and its bacterial degradation products.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="center">Compound</th>
<th colspan="2" align="center">Fish</th>
<th colspan="2" align="center">Daphnids</th>
<th colspan="2" align="center">Green algae</th>
</tr>
<tr>
<th align="center">ED<sub>50</sub>, 96&#xa0;h</th>
<th align="center">LD<sub>50</sub>, 96&#xa0;h</th>
<th align="center">ED<sub>50</sub>, 96&#xa0;h</th>
<th align="center">LD<sub>50</sub>, 48&#xa0;h</th>
<th align="center">ED<sub>50</sub>, 96&#xa0;h</th>
<th align="center">LD<sub>50</sub>, 96&#xa0;h</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">MLX</td>
<td align="center">0.49</td>
<td align="center">494.14</td>
<td align="center">25.38</td>
<td align="center">832.64</td>
<td align="center">8.10</td>
<td align="center">12.73</td>
</tr>
<tr>
<td align="left">5&#x27;-hydroxymethylmeloxicam</td>
<td align="center">0.73</td>
<td align="center">907.16</td>
<td align="center">43.50</td>
<td align="center">1,792.71</td>
<td align="center">11.93</td>
<td align="center">21.69</td>
</tr>
<tr>
<td align="left">5&#x27;-carboxymeloxicam</td>
<td align="center">5.02</td>
<td align="center">4,930.46</td>
<td align="center">255.65</td>
<td align="center">8,131.59</td>
<td align="center">83.26</td>
<td align="center">128.33</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>LD<sub>50</sub>, median lethal dose for acute toxicity; ED<sub>50</sub>, median effect dose for chronic toxicity.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="s3-3">
<title>3.3 Response to MXL exposure</title>
<p>At the early stages of exposure to MLX, we observed a rapid activation of oxygen uptake by aerobic <italic>G</italic>. <italic>alkanivorans</italic> IEGM 1277 versus the control, MLX-free, cultures of this strain for which active respiration occurred after a 3-day lag. The observed increase in the maximum oxygen consumption by MLX-exposed cultures as compared to the control (<xref ref-type="fig" rid="F4">Figure 4</xref>) could be reflect additional energy requirements to cope with oxidative stress caused by MLX. A faster acidification of the medium during MLX degradation than in MLX-free cultures (<xref ref-type="fig" rid="F5">Figure 5A</xref>) could indicate the activation of processes to be involved in MLX decomposition and the accumulation of the MLX metabolites. As MLX was exhausted, the bacterial culture behaved similarly to the control, reaching the similar biomass yield (as judged from OD values) and stationary-phase onset (<xref ref-type="fig" rid="F5">Figure 5B</xref>).</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption>
<p>O<sub>2</sub> consumption by <italic>Gordonia alkanivorans</italic> IEGM 1277 cells with/without MLX.</p>
</caption>
<graphic xlink:href="fbioe-13-1603975-g004.tif">
<alt-text content-type="machine-generated">Graph showing oxygen uptake rate in microliters per hour over 14 days for two cell types. The orange line (IEGM 1277 cells with MLX) peaks at around day three, then decreases and stabilizes. The purple line (IEGM 1277 cells) peaks around days four to six, then declines steadily.</alt-text>
</graphic>
</fig>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption>
<p>Changes in the <bold>(A)</bold> pH and <bold>(B)</bold> OD.</p>
</caption>
<graphic xlink:href="fbioe-13-1603975-g005.tif">
<alt-text content-type="machine-generated">Line graphs labeled A and B show changes over time in two conditions: &#x22;IEGM 1277 cells with MLX&#x22; and &#x22;IEGM 1277 cells,&#x22; along with &#x22;MLX only.&#x22; Graph A depicts pH levels decreasing over 14 days, with MLX levels constant. Graph B shows optical density (OD) increasing for cells with time, while MLX levels remain unchanged.</alt-text>
</graphic>
</fig>
<p>AFM examinations demonstrated that the exposure to MLX after 7 days was followed by a decrease in the surface area-to-volume (S/V) ratio of <italic>G</italic>. <italic>alkanivorans</italic> IEGM 1277 cells (<xref ref-type="table" rid="T4">Table 4</xref>) and its further increase by 14&#xa0;days. The pattern is possibly due to the depletion of MLX from the medium, its more efficient degradation, and the release of less toxic metabolic products (5&#x0027;-hydroxymethyl- and 5&#x0027;-carboxymeloxicam). MLX caused insignificant elongation of bacterial cells: some cells had folds and protrusions (<xref ref-type="fig" rid="F6">Figure 6C</xref>). On the contrary, <italic>G</italic>. <italic>alkanivorans</italic> IEGM 1277 cells in MLX-free cultures showed the relatively smooth and unaltered surface (<xref ref-type="fig" rid="F7">Figures 7A,B</xref>).</p>
<table-wrap id="T4" position="float">
<label>TABLE 4</label>
<caption>
<p>Morphometric changes in <italic>Gordonia alkanivorans</italic> IEGM 1277 bacterial cells under the influence of MLX.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="center">Characteristic</th>
<th colspan="2" align="center">7&#xa0;days</th>
<th colspan="2" align="center">14&#xa0;days</th>
</tr>
<tr>
<th align="center">With MLX</th>
<th align="center">Without MLX</th>
<th align="center">With MLX</th>
<th align="center">Without MLX</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Length, &#xb5;m</td>
<td align="center">1.83 &#xb1; 0.530</td>
<td align="center">1.79 &#xb1; 0.280</td>
<td align="center">1.65 &#xb1; 0.490</td>
<td align="center">1.60 &#xb1; 0.350</td>
</tr>
<tr>
<td align="left">Width, &#xb5;m</td>
<td align="center">0.61 &#xb1; 0.090</td>
<td align="center">0.59 &#xb1; 0.030</td>
<td align="center">0.83 &#xb1; 0.120</td>
<td align="center">0.59 &#xb1; 0.040</td>
</tr>
<tr>
<td align="left">Area (S), &#xb5;m<sup>2</sup>
</td>
<td align="center">37.00 &#xb1; 4.400</td>
<td align="center">53.50 &#xb1; 3.100</td>
<td align="center">39.70 &#xb1; 3.500</td>
<td align="center">14.50 &#xb1; 1.400</td>
</tr>
<tr>
<td align="left">Volume (V), &#xb5;m<sup>3</sup>
</td>
<td align="center">1.36 &#xb1; 0.011</td>
<td align="center">1.23 &#xb1; 0.002</td>
<td align="center">1.72 &#xb1; 0.015</td>
<td align="center">1.21 &#xb1; 0.003</td>
</tr>
<tr>
<td align="left">S/V, &#xb5;m<sup>&#x2212;1</sup>
</td>
<td align="center">27.07 &#xb1; 2.700</td>
<td align="center">43.49 &#xb1; 2.120</td>
<td align="center">22.69 &#xb1; 2.290</td>
<td align="center">12.24 &#xb1; 1.160</td>
</tr>
<tr>
<td align="left">Surface roughness, &#xb5;m</td>
<td align="center">0.12 &#xb1; 0.064</td>
<td align="center">0.24 &#xb1; 0.067</td>
<td align="center">0.11 &#xb1; 0.062</td>
<td align="center">0.16 &#xb1; 0.087</td>
</tr>
</tbody>
</table>
</table-wrap>
<fig id="F6" position="float">
<label>FIGURE 6</label>
<caption>
<p>AFM-images of <italic>Gordonia alkanivorans</italic> IEGM 1277 cells with MLX: <bold>(A)</bold> at 7&#xa0;days; <bold>(B)</bold> at 14&#xa0;days; <bold>(C)</bold> 3D-image; <bold>(D)</bold> profile.</p>
</caption>
<graphic xlink:href="fbioe-13-1603975-g006.tif">
<alt-text content-type="machine-generated">Image A shows a 2D grayscale atomic force microscopy (AFM) image of rod-shaped structures at a scale of 2 micrometers. Image B displays a similar 2D AFM image with a scale of 1 micrometer. Image C is a 3D rendering of the rod-shaped structures, highlighting their topography. Image D is a graph depicting the height profile in nanometers over a 2 micrometer span.</alt-text>
</graphic>
</fig>
<fig id="F7" position="float">
<label>FIGURE 7</label>
<caption>
<p>AFM-images of <italic>Gordonia alkanivorans</italic> IEGM 1277 cells without MLX: <bold>(A)</bold> at 7&#xa0;days; <bold>(B)</bold> at 14&#xa0;days; <bold>(C)</bold> 3D-image; <bold>(D)</bold> profile.</p>
</caption>
<graphic xlink:href="fbioe-13-1603975-g007.tif">
<alt-text content-type="machine-generated">Images A and B show atomic force microscopy images of microbial cells, featuring surface details with scales of 1 micrometer. Image C is a 3D rendering of a single cell, highlighting its topography. Image D contains a graph of height measurements over a span of 2.5 micrometers, displaying variations in surface height in nanometers.</alt-text>
</graphic>
</fig>
<p>EDX-TEM microscopy examinations showed that the majority of cells in cultures with MLX maintained the pool of biogenic elements (carbon, oxygen, phosphorus) and potassium (<xref ref-type="fig" rid="F8">Figure 8B</xref>) as in the control untreated culture (<xref ref-type="fig" rid="F8">Figure 8A</xref>). Only a few cells in the MLX-exposed culture had the reduced level of these elements (<xref ref-type="fig" rid="F8">Figure 8B</xref>, white arrow). It is noteworthy that the bacteria grown in the presence of MLX contained higher amounts of copper than in the control (<xref ref-type="table" rid="T5">Table 5</xref>), and an elevated copper level can be important for the activity of copper-containing monooxygenases and laccases, the enzymes catalysing reactions of oxidation of aromatic compounds (<xref ref-type="bibr" rid="B46">Solomon et al., 2014</xref>).</p>
<fig id="F8" position="float">
<label>FIGURE 8</label>
<caption>
<p>Elemental maps of <italic>Gordonia alkanivorans</italic> IEGM 1277 produced upon TEM-EDX microscopy: <bold>(A)</bold> without MLX; <bold>(B)</bold> with MLX. White arrows indicate a cell with depleted pools of some biogenic elements.</p>
</caption>
<graphic xlink:href="fbioe-13-1603975-g008.tif">
<alt-text content-type="machine-generated">Two rows of electron microscopy images labeled A and B, showing elemental distributions. Top row (A) illustrates elongated shapes; bottom row (B) shows clustered forms, each analyzed for elements: Carbon (C), Oxygen (O), Sodium (Na), Phosphorus (P), Potassium (K), and Calcium (Ca). Each element is highlighted in different colors, with scales marked at 2.5 micrometers.</alt-text>
</graphic>
</fig>
<table-wrap id="T5" position="float">
<label>TABLE 5</label>
<caption>
<p>The contents of chemical elements as derived from EDX-spectral mapping of whole fields with cells and cell-free space for <italic>Gordonia alkanivorans</italic> IEGM 1277 cultures with/without MLX.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Spectrum name</th>
<th align="center">C</th>
<th align="center">O</th>
<th align="center">Na</th>
<th align="center">Si</th>
<th align="center">P</th>
<th align="center">S</th>
<th align="center">K</th>
<th align="center">Ca</th>
<th align="center">Cu</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Without MLX</td>
<td align="center">69.55</td>
<td align="center">8.49</td>
<td align="center">5.60</td>
<td align="center">0.68</td>
<td align="center">1.78</td>
<td align="center">0.34</td>
<td align="center">1.94</td>
<td align="center">0.79</td>
<td align="center">5.43</td>
</tr>
<tr>
<td align="left">With MLX</td>
<td align="center">81.78</td>
<td align="center">6.02</td>
<td align="center">0.43</td>
<td align="center">0.65</td>
<td align="center">0.48</td>
<td align="center">0.12</td>
<td align="center">0.80</td>
<td align="center">0.24</td>
<td align="center">9.30</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>The modification of the elemental composition of <italic>Gordonia</italic> was accompanied by a change in the biophysical parameter of bacterial cells known as the electrophoretic potential, which depends on the composition of the cytoplasmic membrane and the physiological state of the cells. Upon measuring the &#x3b6;-potential of control and MLX-exposed cells, a significant shift of the mean &#x3b6;-potential to the negative region by 15.12&#xa0;mV, from &#x2212;6.18 &#xb1; 0.200&#xa0;mV to &#x2212;21.300 &#xb1; 0.094&#xa0;mV (<xref ref-type="fig" rid="F9">Figure 9</xref>), was revealed. The increase in the absolute value of the electronegativity &#x3b6;-potential indicated the relative stability of a cellular system in the presence of MLX.</p>
<fig id="F9" position="float">
<label>FIGURE 9</label>
<caption>
<p>Changes in the &#x3b6;-potential of <italic>Gordonia alkanivorans</italic> IEGM 1277 with/without MLX.</p>
</caption>
<graphic xlink:href="fbioe-13-1603975-g009.tif">
<alt-text content-type="machine-generated">Graph showing zeta potential distribution for IEGM 1277 with and without MLX. The x-axis represents zeta potential in millivolts, ranging from -50 to 100. The y-axis shows total counts, peaking at 10,000. Two peaks are visible: orange for IEGM 1277 with MLX around -21 mV, and purple for without MLX near -6 mV.</alt-text>
</graphic>
</fig>
<p>Comparative thin section TEM examinations proved the morphological integrity of cells in the control (<xref ref-type="fig" rid="F10">Figure 10A</xref>) and MLX-exposed (<xref ref-type="fig" rid="F10">Figure 10B</xref>) <italic>G</italic>. <italic>alkanivorans</italic> IEGM 1277 cultures as judged from the intact cell wall and intracytoplasmic structures. When grown in the presence of MLX, some cells showed the thick capsular layer with small granules around the cell wall and electron-dense particles to be composed of polyphosphate and electron-transparent droplets (<xref ref-type="fig" rid="F10">Figure 10B</xref>) containing lipids, as supported upon staining with Nile Red (<xref ref-type="fig" rid="F10">Figure 10B</xref>, insert). In the control cells, lipid droplets were absent, as well as electron-dense intracytoplasmic granules (<xref ref-type="fig" rid="F10">Figure 10A</xref>).</p>
<fig id="F10" position="float">
<label>FIGURE 10</label>
<caption>
<p>Transmission electron and fluorescent microscopy of <italic>Gordonia alkanivorans</italic> IEGM 1277 cells: <bold>(A)</bold> without MLX; <bold>(B)</bold> with MLX. Designations: LD&#x2013;lipid droplets; PP&#x2013;polyphosphate particles; CW&#x2013;cell wall. Inserts to <bold>(A,B)</bold> shows images of cells after staining with Nile Red.</p>
</caption>
<graphic xlink:href="fbioe-13-1603975-g010.tif">
<alt-text content-type="machine-generated">Panel A shows a transmission electron microscope image of a rod-shaped bacterium with labeled cell wall (CW) and an inset of fluorescent orange spots. Panel B displays a similar bacterium with labeled lipid droplet (LD) and polar pocket (PP), along with an inset showing fluorescent yellow spots. Both panels feature a scale bar of two hundred nanometers.</alt-text>
</graphic>
</fig>
<p>Thus, the population was heterogeneous, with a substantial part of it tolerating the presence of MLX. The identified changes in <italic>Gordonia</italic> under the influence of MLX highlight the complexity of interactions with bacterial cells, as well as the need for further thorough investigation of the adaptive mechanisms developing in response to the action of toxic agents.</p>
</sec>
<sec id="s3-4">
<title>3.4 Full-genome sequencing</title>
<p>Full-genome sequencing of <italic>G</italic>. <italic>alkanivorans</italic> IEGM 1277 revealed features of the genome of the active MLX biodegrador (<xref ref-type="table" rid="T6">Table 6</xref>). The full-genome sequence is available in the DDBJ/ENA/GenBank databases under the numbers <ext-link ext-link-type="uri" xlink:href="https://www.ncbi.nlm.nih.gov/Traces/wgs/JASIRQ01?display=contigs">JASIRQ010000001-JASIRQ010000143</ext-link>. The genome size of IEGM 1277 was 5.1 Mb, the content of GC formed the majority (67.5%) of the genome in strain IEGM 1277. The percentage ratio of sequences with known and unknown function was 20:80, respectively. According to the obtained genomic data, chromosome IEGM 1277 contained 8 distinct regions (nucleotide sequences) responsible for encoding P450-dependent monooxygenases (<xref ref-type="table" rid="T7">Table 7</xref>). <xref ref-type="table" rid="T8">Table 8</xref> presents the results of the genes and regulatory elements analysis associated with CYP450. Sequences encoding transcriptional regulators have been identified in the adjacent regions for 8 genes in this family, either in close proximity or immediately upstream of them. Cytochrome partner proteins, such as ferredoxin and ferredoxin-reductase, were found only in the vicinity of CYP450 genes No. 2, 3, 4, and 8 (<xref ref-type="bibr" rid="B51">Ugalde et al., 2018</xref>).</p>
<table-wrap id="T6" position="float">
<label>TABLE 6</label>
<caption>
<p>Genome features of <italic>Gordonia alkanivorans</italic> IEGM 1277<xref ref-type="table-fn" rid="Tfn1">&#x2a;</xref>.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Attribute</th>
<th align="center">
<italic>G</italic>. <italic>alkanivorans</italic> IEGM 1277</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Genome size, bp</td>
<td align="center">5,116,883</td>
</tr>
<tr>
<td align="left">GC content, %</td>
<td align="center">67.5</td>
</tr>
<tr>
<td align="left">N50</td>
<td align="center">148,056</td>
</tr>
<tr>
<td align="left">L50</td>
<td align="center">10</td>
</tr>
<tr>
<td align="left">Number of contigs</td>
<td align="center">143</td>
</tr>
<tr>
<td align="left">Genes (total)</td>
<td align="center">4,762</td>
</tr>
<tr>
<td align="left">Genes (coding)</td>
<td align="center">4,591</td>
</tr>
<tr>
<td align="left">CDSs</td>
<td align="center">4,707</td>
</tr>
<tr>
<td align="left">RNA</td>
<td align="center">55</td>
</tr>
<tr>
<td align="left">tRNAs</td>
<td align="center">48</td>
</tr>
<tr>
<td align="left">ncRNAs</td>
<td align="center">3</td>
</tr>
<tr>
<td align="left">Pseudo genes</td>
<td align="center">116</td>
</tr>
<tr>
<td align="left">Genome coverage</td>
<td align="center">672&#xd7;</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="Tfn1">
<label>&#x2a;</label>
<p>According to the onlne service NCBI.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<table-wrap id="T7" position="float">
<label>TABLE 7</label>
<caption>
<p>Genes encoding CYP450 enzymes found in the <italic>Gordonia alkanivorans</italic> IEGM 1277 genome.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Gene no.</th>
<th align="center">Contig ID</th>
<th align="center">Gene location</th>
<th align="center">Amplicon size, bp</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">1</td>
<td align="center">NZ_JASIRQ010000002.1</td>
<td align="center">323087&#x2013;324397</td>
<td align="center">1,310</td>
</tr>
<tr>
<td align="left">2</td>
<td align="center">NZ_JASIRQ010000004.1</td>
<td align="center">94170&#x2013;92782</td>
<td align="center">1,388</td>
</tr>
<tr>
<td align="left">3</td>
<td align="center">NZ_JASIRQ010000005.1</td>
<td align="center">227409&#x2013;226072</td>
<td align="center">1,337</td>
</tr>
<tr>
<td align="left">4</td>
<td align="center">NZ_JASIRQ010000008.1</td>
<td align="center">163169&#x2013;161919</td>
<td align="center">1,250</td>
</tr>
<tr>
<td align="left">5</td>
<td align="center">NZ_JASIRQ010000013.1</td>
<td align="center">115887&#x2013;117302</td>
<td align="center">1,415</td>
</tr>
<tr>
<td align="left">6</td>
<td align="center">NZ_JASIRQ010000015.1</td>
<td align="center">29706&#x2013;28456</td>
<td align="center">1,250</td>
</tr>
<tr>
<td align="left">7</td>
<td align="center">NZ_JASIRQ010000020.1</td>
<td align="center">32053&#x2013;33330</td>
<td align="center">1,277</td>
</tr>
<tr>
<td align="left">8</td>
<td align="center">NZ_JASIRQ010000049.1</td>
<td align="center">1683&#x2013;3,074</td>
<td align="center">1,391</td>
</tr>
</tbody>
</table>
</table-wrap>
<table-wrap id="T8" position="float">
<label>TABLE 8</label>
<caption>
<p>Genetic surroundings of genes encoding CYP450 enzymes in <italic>Gordonia alkanivorans</italic> IEGM 1277.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="center">Gene no.</th>
<th colspan="2" align="center">Nearby genes</th>
</tr>
<tr>
<th align="center">Upstream transcriptional regulators</th>
<th align="center">Proteins</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">1</td>
<td align="center">AcrR family</td>
<td align="center">Enoyl-CoA hydratase; monooxygenase; oxygenase; NADH:flavin oxidoreductase/NADH oxidase; cell wall-binding protein</td>
</tr>
<tr>
<td align="left">2</td>
<td align="center">AcrR family</td>
<td align="center">Ferredoxin reductases; ferredoxin, 2Fe-2S; glyoxalase/bleomycin resistance protein/dioxygenase</td>
</tr>
<tr>
<td align="left">3</td>
<td align="center">AcrR family</td>
<td align="center">Ferredoxin reductase; oxidoreductase, dehydrogenase/reductases; O-succinylbenzoate synthase</td>
</tr>
<tr>
<td align="left">4</td>
<td align="center">GntR family</td>
<td align="center">Ferredoxin reductases; ferredoxin, 2Fe-2S; dehydrogenases with different specificities; lipase</td>
</tr>
<tr>
<td align="left">5</td>
<td align="center">AraC family</td>
<td align="center">Monooxygenase; lyase</td>
</tr>
<tr>
<td align="left">6</td>
<td align="center">LuxR family</td>
<td align="center">Esterase; 3-hydroxybutyryl-CoA dehydrogenase; 3-hydroxyacyl-CoA dehydrogenase</td>
</tr>
<tr>
<td align="left">7</td>
<td align="center">AcrR family</td>
<td align="center">Alcohol dehydrogenase; cyclase; aldehyde dehydrogenase</td>
</tr>
<tr>
<td align="left">8</td>
<td align="center">No</td>
<td align="center">Ferredoxin reductase; ferredoxin, 2Fe-2S; Na<sup>&#x2b;</sup>/H<sup>&#x2b;</sup> antiporter NhaA type</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>Using inhibitors of CYP450 enzyme activity, it has been confirmed that the oxidation process of MLX was catalysed by one of the enzyme complexes. Adding 1-aminobenzotriazole at concentrations ranging from 0.1 to 1&#xa0;mM stopped the process of MLX biodegradation by IEGM 1277 cells, as evidenced by the presence of MLX in the post-culture medium after 14&#xa0;days of exposure. This confirmed that the process of MLX biodegradation could be due to the activity of cytochrome P450-dependent oxygenases.</p>
<p>The findings extend the understanding of the molecular genetic basis of MLX biodegradation by <italic>Gordonia</italic> actinomycetes and set the stage for further analysis of gene expression levels to identify genes and enzymes that enhance the oxidation efficiency of MLX.</p>
</sec>
</sec>
<sec sec-type="discussion" id="s4">
<title>4 Discussion</title>
<p>Our study corroborates previous findings that underscore the substantial potential of microorganisms in the bioremediation of diverse pollutants, including pesticides, mycotoxins, biodegradable plastics, and heavy metals (<xref ref-type="bibr" rid="B24">Litvinenko, 2019</xref>; <xref ref-type="bibr" rid="B49">Taheur et al., 2019</xref>; <xref ref-type="bibr" rid="B38">Ram&#xed;rez et al., 2023</xref>; <xref ref-type="bibr" rid="B34">Payanthoth et al., 2024</xref>). Understanding the biodegradation of specific toxicants necessitates detailed investigation into the underlying microbial and enzymatic mechanisms.</p>
<p>The isolation and characterisation of bacterial strains such as <italic>B. subtilis</italic> and <italic>B. megaterium</italic> (<xref ref-type="bibr" rid="B59">Xia et al., 2017</xref>; <xref ref-type="bibr" rid="B43">Shang et al., 2019</xref>), alongside the yeast <italic>Cryptococcus podzolicus</italic> (<xref ref-type="bibr" rid="B54">Wei et al., 2022</xref>), capable of degrading mycotoxins, provide valuable insights applicable to another challenge of pharmpollutant bioremediation. Similar to mycotoxins, many pharmaceutical compounds exhibit persistence and toxicity in the environment, necessitating efficient microbial degradation strategies. The elucidation of factors influencing mycotoxin biotransformation (including substrate concentration, temperature, pH, metal ions, pollutant source, and organic acids) via recombinant enzymes such as aldo-keto reductase from <italic>Meyerozyma guilliermondii</italic> (<xref ref-type="bibr" rid="B63">Zhang et al., 2024</xref>), alongside transcriptomic analyses revealing microbial response pathways (<xref ref-type="bibr" rid="B54">Wei et al., 2022</xref>), underscores the complexity and specificity of microbial detoxification mechanisms. These findings highlight the critical role of microbial communities and enzymatic systems in adapting to and transforming structurally diverse xenobiotics, including MLX. Understanding such parameters is essential for optimising bioremediation processes.</p>
<p>Moreover, the efficiency of degrading recalcitrant xenobiotics such as MLX varies significantly between ecosystems, influenced by substrate properties, environmental conditions, and microbial community composition (<xref ref-type="bibr" rid="B35">Prasad et al., 2009</xref>; <xref ref-type="bibr" rid="B36">Prasad et al., 2011</xref>). Consistent with observations in plastic biodegradation (<xref ref-type="bibr" rid="B34">Payanthoth et al., 2024</xref>), soil ecosystems typically harbour more diverse and metabolically versatile microbial assemblages compared to aquatic environments, enabling more rapid and complete degradation. This pattern extends to pharmaceuticals, where soil microbiota exhibit enhanced capacity for the mineralisation of anthropogenic micropollutants (<xref ref-type="bibr" rid="B18">Ivshina et al., 2015</xref>; <xref ref-type="bibr" rid="B20">Ivshina et al., 2019</xref>; <xref ref-type="bibr" rid="B19">Ivshina et al., 2021</xref>). Environmental factors including redox potential, nutrient availability, and temperature further modulate microbial activity and degradation kinetics, emphasising the necessity for ecosystem-specific bioremediation strategies. Integrating these ecological and biochemical insights is therefore essential for the development of effective bacterial-mediated biodegradation approaches targeting MLX and other pharmaceutical contaminants in diverse environmental matrices.</p>
<p>The main novel result of our study is the demonstrated ability of <italic>Gordonia sensu stricto</italic> to degrade MLX completely under the selected conditions. Our choice of the genus <italic>Gordonia</italic> for MLX biodegradation was informed by its phylogenetic proximity to the genus <italic>Rhodococcus</italic>, both classified within the order <italic>Mycobacteriales</italic>, class <italic>Actinomycetes</italic> (<xref ref-type="bibr" rid="B12">Goodfellow, 2014</xref>). Previous studies have demonstrated the capacity of <italic>Rhodococcus</italic> spp. to decompose drotaverine (<xref ref-type="bibr" rid="B18">Ivshina et al., 2015</xref>), diclofenac (<xref ref-type="bibr" rid="B20">Ivshina et al., 2019</xref>), and ibuprofen efficiently (<xref ref-type="bibr" rid="B19">Ivshina et al., 2021</xref>), supporting the hypothesis that <italic>Gordonia</italic> spp. Could exhibit similar metabolic capabilities toward NSAIDs. This hypothesis was substantiated in the present work, where <italic>G. alkanivorans</italic> IEGM 1277 effectively degraded MLX under the tested conditions.</p>
<p>Our study (<xref ref-type="table" rid="T6">Tables 6</xref>,<xref ref-type="table" rid="T7">7</xref>) has revealed the presence of distinct genes, responsible for encoding P450-dependent enzymes, the most important players in the process of biological oxidation of drugs, in the genome of <italic>G. alkanivorans</italic> IEGM 1277 (<xref ref-type="bibr" rid="B14">Guengerich, 2006</xref>). Based on these data (<xref ref-type="table" rid="T8">Table 8</xref>), we hypothesised that the genes encoding these CYP450s (No. 2, 3, 4, 8), ferredoxin, and ferredoxin-reductase formed a gene cluster that was potentially expressed as a polycistronic transcript and that these proteins are involved in a separate metabolic process, likely related to MLX oxidation. It is noteworthy that genes encoding CYP450 were also found in the genome of <italic>R. rhodochrous</italic> IEGM 757, the efficient biotransformation agent of oleanolic acid &#x2013; a recalcitrant triterpenoid substance (<xref ref-type="bibr" rid="B26">Luchnikova et al., 2022</xref>). Other cytochromes in IEGM 1277 may be involved in complex biochemical and metabolic processes, allowing bacteria to survive and adapt in the absence of toxic MLX. These processes may involve the catabolism of lipids, fatty acids or amino acids, as well as the synthesis and maintenance of cell wall integrity, as evidenced by the presence of genes encoding the relevant enzymes. Other metabolic processes may be associated with the neutralisation of toxic organic compounds, as sequences coding for various transport proteins and other oxidoreductases have been found nearby the CYP450 genes. Transcriptomic analysis by <xref ref-type="bibr" rid="B54">Wei et al. (2022)</xref> demonstrated that <italic>C. podzolicus</italic> Y3 upregulates cytochrome P450 enzymes upon exposure to ochratoxin A, underscoring their central function in oxidative mycotoxin degradation. Concurrently, zinc finger proteins regulate genes associated with detoxification and stress responses, while heat shock protein 70 maintains cellular integrity under toxin-induced stress. In this regard, cytochromes play an important role since cytochromes catalyse the initial enzymatic breakdown, supported by regulatory and protective proteins. It is plausible that analogous molecular adaptation mechanisms are exhibited by <italic>Gordonia</italic> in response to pharmpollutants exposure. Although this study focused on a limited subset of actinomycete strains as potential MLX degraders, further systematic investigation is warranted to comprehensively assess the biodegradation capabilities across a broader microbial spectrum.</p>
<p>Properly selecting MLX-tolerant and degrading strains (<xref ref-type="table" rid="T1">Tables 1</xref>,<xref ref-type="table" rid="T2">2</xref>) from twenty <italic>Gordonia</italic> representatives was an important step: only a few strains could remove MLX, with <italic>G</italic>. <italic>alkanivorans</italic> IEGM 1277 being the most effective<italic>.</italic> Different strains within the same species, e.g., <italic>G</italic>. <italic>alkanivorans,</italic> displayed different rates of MLX decomposition (<xref ref-type="table" rid="T2">Table 2</xref>), which is consistent with the reported results of MLX biotransformation by various <italic>B. subtilis</italic> strains and representatives of the <italic>Pseudomonas</italic> genus (<xref ref-type="bibr" rid="B35">Prasad et al., 2009</xref>). Due to the limited number of reports on the microbial degradation of MLX, it is not possible to compare the capabilities of various microorganisms as its destructors. Complete disappearance of MLX (10&#xa0;mg/L) was achieved over 14&#xa0;days of cultivation in the RS mineral medium in our study. Using the selected <italic>B. subtilis</italic> and <italic>P. putida</italic> strains enabled the removal of 27%&#x2013;41% of MLX from the initial 20&#xa0;mg/L level over a shorter cultivation period in a nutritionally rich broth (<xref ref-type="bibr" rid="B35">Prasad et al., 2009</xref>). Furthermore, the efficiency of MLX transformation by the fungus <italic>Cunninghamella blakesleeana</italic> depended upon the medium composition: the maximum (ca. 80%) biotransformation occurred when the microorganism was cultivated in the medium containing glucose as the carbon source and ammonium nitrate as the nitrogen source (<xref ref-type="bibr" rid="B36">Prasad et al., 2011</xref>).</p>
<p>The RS medium was selected for this study due to its cost-effectiveness, widespread use in actinomycete research, and demonstrated efficacy in supporting the degradation of ibuprofen by related <italic>Rhodococcus</italic> species (<xref ref-type="bibr" rid="B19">Ivshina et al., 2021</xref>). Its composition, including readily available ammonium sulphate, dipotassium phosphate, and sufficient iron concentrations essential for the activity of cytochromes and oxidoreductases (<xref ref-type="bibr" rid="B29">Meenakshi et al., 2024</xref>; <xref ref-type="bibr" rid="B58">Wu et al., 2022</xref>). Furthermore, the use of a simple mineral medium, as opposed to complex organic alternatives, facilitates the isolation of valuable metabolites generated during the biodegradation of target compounds.</p>
<p>Concentrations of MLX in environmental samples have previously been reported in the limited number of papers, ranging from nanograms to micrograms per litre (<xref ref-type="bibr" rid="B21">Jim&#xe9;nez et al., 2018</xref>; <xref ref-type="bibr" rid="B13">Gros et al., 2012</xref>), as in the case of other pharmaceuticals (<xref ref-type="bibr" rid="B4">Boxall and Brooks, 2024</xref>). However, industrial processes can result in localised, transient spikes in the concentrations of pharmaceutical compounds which can be orders of magnitude higher than environmental levels (<xref ref-type="bibr" rid="B33">Pal, 2017</xref>). Therefore, the use of MLX in concentrations exceeding the environmental levels, as in this study and the previous studies (<xref ref-type="bibr" rid="B35">Prasad et al., 2009</xref>; <xref ref-type="bibr" rid="B36">Prasad et al., 2011</xref>), is justified in terms of worst-case environmental MLX contamination and of evaluations of the upper limit of bacterial tolerance and adaptation. The concentration of MLX in the medium should also be selected. Initial 20&#x2013;50&#xa0;mg/L levels in the medium were not suitable; the concentration of 10&#xa0;mg/L turned out to be optimal for MLX biodegradation by <italic>Gordonia</italic> strains, as well as even for the 80% chemical degradation of MLX using the sonophotocatalytic system with ferrous tungstate (<xref ref-type="bibr" rid="B60">Xu et al., 2021</xref>). Therefore, the efficacy of the microbial utilisation of MLX depends on the nature of the microorganism used, the cultivation conditions, and the concentration of the target substance. The disappearance of MLX was correlated with its biodegradation into 5&#x27;-hydroxymethylmeloxicam and 5&#x27;-carboxymeloxicam (<xref ref-type="fig" rid="F2">Figure 2</xref>), consistent with metabolites previously detected in (<xref ref-type="bibr" rid="B35">Prasad et al., 2009</xref>; <xref ref-type="bibr" rid="B36">Prasad et al., 2011</xref>), both of which exhibit predicted low toxicity (<xref ref-type="table" rid="T3">Table 3</xref>). It is noteworthy that microbial removal of toxic compounds does not invariably entail enzymatic detoxification; for instance, the elimination of ochratoxin A by <italic>B. megaterium</italic> has been attributed to cellular adsorption mechanisms rather than enzymatic degradation (<xref ref-type="bibr" rid="B43">Shang et al., 2019</xref>).</p>
<p>Overall, the results of our study, on the one hand, demonstrated the integrity of the majority of <italic>G. alkanivorans</italic> IEGM 1277 cells developing in the presence of MLX. This was evidenced by electron microscopy visualising intact cells and subcellular structures (<xref ref-type="fig" rid="F10">Figure 10</xref>), as well as a stable negative &#x3b6;-potential (<xref ref-type="fig" rid="F9">Figure 9</xref>), indicating the preservation of the mycolic acid layer in the cell wall (<xref ref-type="bibr" rid="B57">Wilson et al., 2001</xref>). In addition, TEM-EDX-based analysis revealed no change in nutrient pools in most MLX-adapted cells; a few cells lost carbon, phosphorus, sulphur, and potassium (<xref ref-type="table" rid="T5">Table 5</xref>; <xref ref-type="fig" rid="F8">Figure 8</xref>). The depletion of these and other chemical element stores, which is a manifestation of the cytotoxic effect, has been demonstrated on mycobacteria subjected to harsh antibiotic therapy (<xref ref-type="bibr" rid="B40">Salina et al., 2024</xref>).</p>
<p>On the other hand, physiological assays (<xref ref-type="fig" rid="F4">Figures 4</xref>, <xref ref-type="fig" rid="F5">5</xref>) and AFM studies (<xref ref-type="fig" rid="F6">Figure 6</xref>) demonstrate the flexible response of <italic>G. alkanivorans</italic> IEGM 1277 to the presence of MLX, as well as the return of cells to baseline as MLX is depleted. The observed slight cell elongation (<xref ref-type="table" rid="T4">Table 4</xref>) may be due to impaired peptidoglycan synthesis, a similar morphological feature characteristic of cells exposed to some antibiotics (<xref ref-type="bibr" rid="B37">Punchenko et al., 2024</xref>). The extracellular substance visible in AFM-images (<xref ref-type="fig" rid="F6">Figure 6</xref>) or thin sections (<xref ref-type="fig" rid="F10">Figure 10</xref>) could contain biogenic surfactants or their mixture with <italic>n</italic>-hexadecane and MLX. Biosurfactant synthesis enhances substrate bioavailability and is considered a mechanism by which cells adapt to the effects of hydrophobic MLX (<xref ref-type="bibr" rid="B61">Yan et al., 2024</xref>). Among the specific morphological features of cells exposed to MLX is the appearance of intracytoplasmic droplets with lipid components (<xref ref-type="fig" rid="F10">Figure 10</xref>). These droplets may serve as a &#x2018;storehouse&#x2019; for carbon sources that are also utilised in the synthesis of mycolic acids in <italic>Gordonia</italic>. This process contributes to the protective function of the cell wall against toxicants (<xref ref-type="bibr" rid="B27">Marrakchi et al., 2014</xref>). In addition to acting as a carbon reserve, lipids may also be involved in protecting DNA from degradation (<xref ref-type="bibr" rid="B62">Zhang et al., 2017</xref>). Similar ultrastructural changes were observed in members of the genus <italic>Rhodococcus</italic> developing in the presence of different NSAIDs (<xref ref-type="bibr" rid="B20">Ivshina et al., 2019</xref>; <xref ref-type="bibr" rid="B19">Ivshina et al., 2021</xref>) or oleanolic acid (<xref ref-type="bibr" rid="B26">Luchnikova et al., 2022</xref>).</p>
</sec>
<sec sec-type="conclusion" id="s5">
<title>5 Conclusion</title>
<p>Screening of 20 actinomycetes strains of the <italic>Gordonia</italic> genus maintained in the Regional Specialised Collection of Alkanotrophic Microorganisms (<ext-link ext-link-type="uri" xlink:href="http://www.iegmcol.ru">www.iegmcol.ru</ext-link>) revealed 5 strains with high (MIC &#x2265;5.000&#xa0;g/L) tolerance to MLX. No direct correlation was found between the resistance of the strains to the ecotoxicant and their species affiliation.</p>
<p>The highest enzymatic activity against MLX was exhibited by <italic>G</italic>. <italic>alkanivorans</italic> IEGM 1277, which was capable of completely degrading MLX (10&#xa0;mg/L) in the presence of <italic>n</italic>-hexadecane for 14&#xa0;days. The presence of MLX in the cultivation medium of <italic>Gordonia</italic> induced metabolic, morphometric, and ultrastructural changes in <italic>G</italic>. <italic>alkanivorans</italic> IEGM 1277 cells, which could be considered as bacterial adaptive mechanisms and, consequently, an increase in their resistance to the toxic effects of the pharmaceutical pollutant. According to the chemical structure metabolites analysis of the strain IEGM 1277, the most common molecules were 5&#x27;-hydroxymethylmeloxicam and 5&#x27;-carboxymeloxicam, which were found to be substantially less toxic than MLX. Gene clusters for the synthesis of P450-dependent monooxygenases responsible for the initial oxidation of the MLX molecule were identified by genomic mining. The novel and significant finding of this study is that the representative of the genus <italic>Gordonia</italic> is capable of efficient biodegradation of MLX. The findings of this study offer valuable insights into the ecological function of this group of actinomycetes as subjects of ecological rehabilitation in the detoxification of natural ecosystems. The study establishes the foundation for the implementation of novel technical solutions for advanced wastewater treatment in pharmaceutical production and the disposal of dangerous pharmaceutical waste.</p>
</sec>
</body>
<back>
<sec sec-type="data-availability" id="s6">
<title>Data availability statement</title>
<p>The datasets presented in this study can be found in online repositories. The names of the repository/repositories and accession number(s) can be found below: <ext-link ext-link-type="uri" xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="https://www.ncbi.nlm.nih.gov/">https://www.ncbi.nlm.nih.gov/</ext-link>, <ext-link ext-link-type="uri" xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="https://www.ncbi.nlm.nih.gov/Traces/wgs/JASIRQ01?display=contigs">JASIRQ010000001-JASIRQ010000143.</ext-link>
</p>
</sec>
<sec sec-type="author-contributions" id="s7">
<title>Author contributions</title>
<p>ST: Formal Analysis, Investigation, Software, Validation, Visualization, Writing &#x2013; original draft, Writing &#x2013; review and editing. NK: Investigation, Writing &#x2013; review and editing. VS: Investigation, Writing &#x2013; review and editing. AM: Investigation, Writing &#x2013; review and editing. II: Conceptualization, Data curation, Funding acquisition, Methodology, Project administration, Resources, Supervision, Writing &#x2013; original draft, Writing &#x2013; review and editing.</p>
</sec>
<sec sec-type="funding-information" id="s8">
<title>Funding</title>
<p>The author(s) declare that financial support was received for the research and/or publication of this article. This work was supported by the state assignments (no. 124020500028-4 Biodiversity of microorganisms of anthropogenic polluted ecosystems and functional and genetic mechanisms of their adaptation to stressful environmental conditions and no. 122040800164-6 Microbiology of innovative biotechnologies).</p>
</sec>
<ack>
<p>The work was carried out using the equipment of The Core Facilities Centers &#x201c;Regional Specialised Collection of Alkanotrophic Microorganisms&#x201d; and &#x201c;Research of Materials and Matter&#x201d; at PFRC UB RAS. TEM microscopy and EDX analysis were performed in the Core Facility Center &#x201c;UNIQEM Collection&#x201d; at Research Center of Biotechnology, RAS.</p>
</ack>
<sec sec-type="COI-statement" id="s9">
<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 sec-type="ai-statement" id="s10">
<title>Generative AI statement</title>
<p>The author(s) declare that no Generative AI was used in the creation of this manuscript.</p>
</sec>
<sec sec-type="disclaimer" id="s11">
<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>
</sec>
<ref-list>
<title>References</title>
<ref id="B1">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Ahmed</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Khanna</surname>
<given-names>D.</given-names>
</name>
<name>
<surname>Furst</surname>
<given-names>D.</given-names>
</name>
</person-group> (<year>2005</year>). <article-title>Meloxicam in rheumatoid arthritis</article-title>. <source>Expert Opin. Drug Metab. Toxicol.</source> <volume>1</volume>, <fpage>739</fpage>&#x2013;<lpage>751</lpage>. <pub-id pub-id-type="doi">10.1517/17425255.1.4.739</pub-id>
</citation>
</ref>
<ref id="B2">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Alotaibi</surname>
<given-names>F.</given-names>
</name>
<name>
<surname>St-Arnaud</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Hijri</surname>
<given-names>M.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>In-depth characterization of plant growth promotion potentials of selected alkanes-degrading plant growth-promoting bacterial isolates</article-title>. <source>Front. Microbiol.</source> <volume>13</volume>, <fpage>863702</fpage>. <pub-id pub-id-type="doi">10.3389/fmicb.2022.863702</pub-id>
</citation>
</ref>
<ref id="B3">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Bekker</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Kloepping</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Collingwood</surname>
<given-names>S.</given-names>
</name>
</person-group> (<year>2018</year>). <article-title>Meloxicam in the management of post-operative pain: Narrative review</article-title>. <source>J. Anaesthesiol. Clin. Pharmacol.</source> <volume>34</volume>, <fpage>450</fpage>&#x2013;<lpage>457</lpage>. <pub-id pub-id-type="doi">10.4103/joacp.joacp_133_18</pub-id>
</citation>
</ref>
<ref id="B4">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Boxall</surname>
<given-names>A. B. A.</given-names>
</name>
<name>
<surname>Brooks</surname>
<given-names>W. B.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>Pharmaceuticals and personal care products in the environment: what progress has been made in addressing the big research questions?</article-title> <source>Environ. Toxicol. Chem.</source> <volume>43</volume>, <fpage>481</fpage>&#x2013;<lpage>487</lpage>. <pub-id pub-id-type="doi">10.1002/etc.5827</pub-id>
</citation>
</ref>
<ref id="B5">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Carter</surname>
<given-names>L. J.</given-names>
</name>
<name>
<surname>Armitage</surname>
<given-names>J. M.</given-names>
</name>
<name>
<surname>Brooks</surname>
<given-names>B. W.</given-names>
</name>
<name>
<surname>Nichols</surname>
<given-names>J. W.</given-names>
</name>
<name>
<surname>Trapp</surname>
<given-names>S.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>Predicting the accumulation of ionizable pharmaceuticals and personal care products in aquatic and terrestrial organisms</article-title>. <source>Environ. Toxicol. Chem.</source> <volume>43</volume>, <fpage>502</fpage>&#x2013;<lpage>512</lpage>. <pub-id pub-id-type="doi">10.1002/etc.5451</pub-id>
</citation>
</ref>
<ref id="B6">
<citation citation-type="web">
<collab>Catalogue of Strains</collab> (<year>2025</year>). <article-title>Catalogue of strains of regional specialised collection of alkanotrophic microorganisms</article-title>. <comment>Available online at: <ext-link ext-link-type="uri" xlink:href="http://www.iegmcol/strains/index.html">http://www.iegmcol/strains/index.html</ext-link> (Accessed March 17, 2025)</comment>.</citation>
</ref>
<ref id="B7">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Crowther</surname>
<given-names>T. W.</given-names>
</name>
<name>
<surname>Rappuoli</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Corinaldesi</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Danovaro</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Donohue</surname>
<given-names>T. J.</given-names>
</name>
<name>
<surname>Huisman</surname>
<given-names>J.</given-names>
</name>
<etal/>
</person-group> (<year>2024</year>). <article-title>Scientists&#x2019; call to action: Microbes, planetary health, and the sustainable development goals</article-title>. <source>Cell</source> <volume>187</volume>, <fpage>5195</fpage>&#x2013;<lpage>5216</lpage>. <pub-id pub-id-type="doi">10.1016/j.cell.2024.07.051</pub-id>
</citation>
</ref>
<ref id="B8">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Dalal</surname>
<given-names>D.</given-names>
</name>
<name>
<surname>Dubreuil</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Peloquin</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Neogi</surname>
<given-names>T.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Choi</surname>
<given-names>H.</given-names>
</name>
<etal/>
</person-group> (<year>2017</year>). <article-title>Meloxicam and risk of myocardial infarction: a population-based nested case-control study</article-title>. <source>Rheumatol. Int.</source> <volume>37</volume>, <fpage>2071</fpage>&#x2013;<lpage>2078</lpage>. <pub-id pub-id-type="doi">10.1007/s00296-017-3835-x</pub-id>
</citation>
</ref>
<ref id="B9">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>da Silva</surname>
<given-names>J. C. G.</given-names>
</name>
<name>
<surname>Bigolin</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>da Silva</surname>
<given-names>L. C.</given-names>
</name>
<name>
<surname>Sebulsqui Saraiva</surname>
<given-names>T. E.</given-names>
</name>
<name>
<surname>Machado Menezes</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Veiverberg</surname>
<given-names>A.</given-names>
</name>
<etal/>
</person-group> (<year>2020</year>). <article-title>Neurotoxicity evaluation of meloxicam in the alternative <italic>in vivo</italic> model, <italic>Caenorhabditis elegans</italic>
</article-title>. <source>Int. J. Innov. Educ. Res.</source> <volume>8</volume>, <fpage>319</fpage>&#x2013;<lpage>325</lpage>. <pub-id pub-id-type="doi">10.31686/ijier.vol8.iss8.2522</pub-id>
</citation>
</ref>
<ref id="B10">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>da Silva</surname>
<given-names>J. C. G.</given-names>
</name>
<name>
<surname>Dallegrave</surname>
<given-names>E.</given-names>
</name>
<name>
<surname>Rodrigues</surname>
<given-names>G. Z. P.</given-names>
</name>
<name>
<surname>Bigolin</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Neumann</surname>
<given-names>T. M. S. de O.</given-names>
</name>
<name>
<surname>Schuster</surname>
<given-names>A. C.</given-names>
</name>
<etal/>
</person-group> (<year>2022</year>). <article-title>Repeated dose of meloxicam induces genotoxicity and histopathological changes in cardiac tissue of mice</article-title>. <source>Drug Chem. Toxicol.</source> <volume>45</volume>, <fpage>822</fpage>&#x2013;<lpage>833</lpage>. <pub-id pub-id-type="doi">10.1080/01480545.2020.1778018</pub-id>
</citation>
</ref>
<ref id="B11">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Frantsuzova</surname>
<given-names>E.</given-names>
</name>
<name>
<surname>Bogun</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Shishkina</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Vetrova</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Solyanikova</surname>
<given-names>I.</given-names>
</name>
<name>
<surname>Delegan</surname>
<given-names>Y.</given-names>
</name>
</person-group> (<year>2023</year>). <article-title>Insights into the potential role of <italic>Gordonia alkanivorans</italic> strains in biotechnologies</article-title>. <source>Processes</source> <volume>11</volume>, <fpage>3184</fpage>. <pub-id pub-id-type="doi">10.3390/pr11113184</pub-id>
</citation>
</ref>
<ref id="B12">
<citation citation-type="book">
<person-group person-group-type="author">
<name>
<surname>Goodfellow</surname>
<given-names>M.</given-names>
</name>
</person-group> (<year>2014</year>). &#x201c;<article-title>The family <italic>Nocardiaceae</italic>
</article-title>,&#x201d; in <source>The Prokaryotes</source>. Editors <person-group person-group-type="editor">
<name>
<surname>Rosenberg</surname>
<given-names>E.</given-names>
</name>
<name>
<surname>DeLong</surname>
<given-names>E. F.</given-names>
</name>
<name>
<surname>Lory</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Stackebrandt</surname>
<given-names>E.</given-names>
</name>
<name>
<surname>Thompson</surname>
<given-names>F.</given-names>
</name>
</person-group> (<publisher-loc>Berlin, Heidelberg</publisher-loc>: <publisher-name>Springer</publisher-name>). <pub-id pub-id-type="doi">10.1007/978-3-642-30138-4_404</pub-id>
</citation>
</ref>
<ref id="B13">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Gros</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Rodr&#xed;guez-Mozaz</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Barcel&#xf3;</surname>
<given-names>D.</given-names>
</name>
</person-group> (<year>2012</year>). <article-title>Fast and comprehensive multi-residue analysis of a broad range of human and veterinary pharmaceuticals and some of their metabolites in surface and treated waters by ultra-high-performance liquid chromatography coupled to quadrupole-linear ion trap tandem mass spectrometry</article-title>. <source>J. Chromatogr. A</source> <volume>1248</volume>, <fpage>104</fpage>&#x2013;<lpage>121</lpage>. <pub-id pub-id-type="doi">10.1016/j.chroma.2012.05.084</pub-id>
</citation>
</ref>
<ref id="B14">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Guengerich</surname>
<given-names>F. P.</given-names>
</name>
</person-group> (<year>2006</year>). <article-title>Cytochrome P450s and other enzymes in drug metabolism and toxicity</article-title>. <source>AAPS J.</source> <volume>8</volume>, <fpage>E101</fpage>&#x2013;<lpage>E111</lpage>. <pub-id pub-id-type="doi">10.1208/aapsj080112</pub-id>
</citation>
</ref>
<ref id="B15">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Gupta</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Kumar</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Bajpai</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Chaturvedi</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Johri</surname>
<given-names>P.</given-names>
</name>
<name>
<surname>Tiwari</surname>
<given-names>R. K.</given-names>
</name>
<etal/>
</person-group> (<year>2024</year>). <article-title>Pharmaceutically active micropollutants: origin, hazards and removal</article-title>. <source>Front. Microbiol.</source> <volume>15</volume>, <fpage>1339469</fpage>. <pub-id pub-id-type="doi">10.3389/fmicb.2024.1339469</pub-id>
</citation>
</ref>
<ref id="B16">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Herrero-Villar</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Velarde</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Camarero</surname>
<given-names>P. R.</given-names>
</name>
<name>
<surname>Taggart</surname>
<given-names>M. A.</given-names>
</name>
<name>
<surname>Bandeira</surname>
<given-names>V.</given-names>
</name>
<name>
<surname>Fonseca</surname>
<given-names>C.</given-names>
</name>
<etal/>
</person-group> (<year>2020</year>). <article-title>NSAIDs detected in Iberian avian scavengers and carrion after diclofenac registration for veterinary use in Spain</article-title>. <source>Environ. Pollut.</source> <volume>266</volume>, <fpage>115157</fpage>. <pub-id pub-id-type="doi">10.1016/j.envpol.2020.115157</pub-id>
</citation>
</ref>
<ref id="B17">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Huynh</surname>
<given-names>N. C.</given-names>
</name>
<name>
<surname>Nguyen</surname>
<given-names>T. T.</given-names>
</name>
<name>
<surname>Nguyen</surname>
<given-names>D. T.</given-names>
</name>
<name>
<surname>Tran</surname>
<given-names>T. V.</given-names>
</name>
</person-group> (<year>2023</year>). <article-title>Occurrence, toxicity, impact and removal of selected non-steroidal anti-inflammatory drugs (NSAIDs): A review</article-title>. <source>Sci. Total Environ.</source> <volume>10</volume>, <fpage>165317</fpage>. <pub-id pub-id-type="doi">10.1016/j.scitotenv.2023.165317</pub-id>
</citation>
</ref>
<ref id="B18">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Ivshina</surname>
<given-names>I. B.</given-names>
</name>
<name>
<surname>Mukhutdinova</surname>
<given-names>A. N.</given-names>
</name>
<name>
<surname>Tyumina</surname>
<given-names>H. A.</given-names>
</name>
<name>
<surname>Vikhareva</surname>
<given-names>H. V.</given-names>
</name>
<name>
<surname>Suzina</surname>
<given-names>N. E.</given-names>
</name>
<name>
<surname>El&#x2019;-Registan</surname>
<given-names>G. I.</given-names>
</name>
<etal/>
</person-group> (<year>2015</year>). <article-title>Drotaverine hydrochloride degradation using cyst-like dormant cells of <italic>Rhodococcus ruber</italic>
</article-title>. <source>Curr. Microbiol.</source> <volume>70</volume>, <fpage>307</fpage>&#x2013;<lpage>314</lpage>. <pub-id pub-id-type="doi">10.1007/s00284-014-0718-1</pub-id>
</citation>
</ref>
<ref id="B19">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Ivshina</surname>
<given-names>I. B.</given-names>
</name>
<name>
<surname>Tyumina</surname>
<given-names>E. A.</given-names>
</name>
<name>
<surname>Bazhutin</surname>
<given-names>G. A.</given-names>
</name>
<name>
<surname>Vikhareva</surname>
<given-names>E. V.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Response of <italic>Rhodococcus cerastii</italic> IEGM 1278 to toxic effects of ibuprofen</article-title>. <source>PLoS One</source> <volume>16</volume>, <fpage>e0260032</fpage>. <pub-id pub-id-type="doi">10.1371/journal.pone.0260032</pub-id>
</citation>
</ref>
<ref id="B20">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Ivshina</surname>
<given-names>I. B.</given-names>
</name>
<name>
<surname>Tyumina</surname>
<given-names>E. A.</given-names>
</name>
<name>
<surname>Kuzmina</surname>
<given-names>M. V.</given-names>
</name>
<name>
<surname>Vikhareva</surname>
<given-names>E. V.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>Features of diclofenac biodegradation by <italic>Rhodococcus ruber</italic> IEGM 346</article-title>. <source>Sci. Rep.</source> <volume>9</volume>, <fpage>9159</fpage>. <pub-id pub-id-type="doi">10.1038/s41598-019-45732-9</pub-id>
</citation>
</ref>
<ref id="B21">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Jim&#xe9;nez</surname>
<given-names>J. J.</given-names>
</name>
<name>
<surname>Mu&#xf1;oz</surname>
<given-names>B. E.</given-names>
</name>
<name>
<surname>S&#xe1;nchez</surname>
<given-names>M. I.</given-names>
</name>
<name>
<surname>Pardo</surname>
<given-names>R.</given-names>
</name>
</person-group> (<year>2018</year>). <article-title>Forced and long-term degradation assays of tenoxicam, piroxicam and meloxicam in river water. Degradation products and adsorption to sediment</article-title>. <source>Chemosphere</source> <volume>191</volume>, <fpage>903</fpage>&#x2013;<lpage>910</lpage>. <pub-id pub-id-type="doi">10.1016/j.chemosphere.2017.10.056</pub-id>
</citation>
</ref>
<ref id="B22">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Karateev</surname>
<given-names>A. E.</given-names>
</name>
<name>
<surname>Nasonov</surname>
<given-names>E. L.</given-names>
</name>
<name>
<surname>Pogozheva</surname>
<given-names>E. Y.</given-names>
</name>
<name>
<surname>Filatova</surname>
<given-names>E. S.</given-names>
</name>
<name>
<surname>Amirdzhanova</surname>
<given-names>V. N.</given-names>
</name>
<name>
<surname>Nesterenko</surname>
<given-names>V. A.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>An old friend: 25 years of meloxicam use in Russia</article-title>. <source>Rheumatol. Sci. Pract.</source> <volume>59</volume>, <fpage>302</fpage>&#x2013;<lpage>315</lpage>. <pub-id pub-id-type="doi">10.47360/1995-4484-2021-302-315</pub-id>
</citation>
</ref>
<ref id="B23">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Lan</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>N.</given-names>
</name>
<name>
<surname>Liu</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Chen</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Xie</surname>
<given-names>J.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>
<italic>&#x3b5;</italic>-Polylysine inhibits <italic>Shewanella putrefaciens</italic> with membrane disruption and cell damage</article-title>. <source>Molecules</source> <volume>24</volume>, <fpage>3727</fpage>. <pub-id pub-id-type="doi">10.3390/molecules24203727</pub-id>
</citation>
</ref>
<ref id="B24">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Litvinenko</surname>
<given-names>L. V.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>Ability of the <italic>Dietzia, Gordonia</italic> and <italic>Rhodococcus</italic> actinobacteria to accumulate nickel ions</article-title>. <source>Microbiology</source> <volume>88</volume>, <fpage>191</fpage>&#x2013;<lpage>199</lpage>. <pub-id pub-id-type="doi">10.1134/s0026261719020061</pub-id>
</citation>
</ref>
<ref id="B25">
<citation citation-type="web">
<collab>LiverTox</collab> (<year>2025</year>). <article-title>Clinical and research information on drug-induced liver injury</article-title>. <comment>Available online at: <ext-link ext-link-type="uri" xlink:href="https://www.ncbi.nlm.nih.gov/books/NBK547852/">https://www.ncbi.nlm.nih.gov/books/NBK547852/</ext-link> (Accessed March 10, 2025)</comment>.</citation>
</ref>
<ref id="B26">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Luchnikova</surname>
<given-names>N. A.</given-names>
</name>
<name>
<surname>Grishko</surname>
<given-names>V. V.</given-names>
</name>
<name>
<surname>Kostrikina</surname>
<given-names>N. A.</given-names>
</name>
<name>
<surname>Sorokin</surname>
<given-names>V. V.</given-names>
</name>
<name>
<surname>Mulyukin</surname>
<given-names>A. L.</given-names>
</name>
<name>
<surname>Ivshina</surname>
<given-names>I. B.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Biotransformation of oleanolic acid using <italic>Rhodococcus rhodochrous</italic> IEGM 757</article-title>. <source>Catalysts</source> <volume>12</volume>, <fpage>1352</fpage>. <pub-id pub-id-type="doi">10.3390/catal12111352</pub-id>
</citation>
</ref>
<ref id="B27">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Marrakchi</surname>
<given-names>H.</given-names>
</name>
<name>
<surname>Lan&#xe9;elle</surname>
<given-names>M. A.</given-names>
</name>
<name>
<surname>Daff&#xe9;</surname>
<given-names>M.</given-names>
</name>
</person-group> (<year>2014</year>). <article-title>Mycolic acids: structures, biosynthesis, and beyond</article-title>. <source>Chem. Biol.</source> <volume>21</volume>, <fpage>67</fpage>&#x2013;<lpage>85</lpage>. <pub-id pub-id-type="doi">10.1016/j.chembiol.2013.11.011</pub-id>
</citation>
</ref>
<ref id="B28">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Meena</surname>
<given-names>V.</given-names>
</name>
<name>
<surname>Swami</surname>
<given-names>D.</given-names>
</name>
<name>
<surname>Chandel</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Joshi</surname>
<given-names>N.</given-names>
</name>
<name>
<surname>Prasher</surname>
<given-names>S. O.</given-names>
</name>
</person-group> (<year>2025</year>). <article-title>Selected emerging contaminants in water: Global occurrence, existing treatment technologies, regulations and associated risk</article-title>. <source>J. Hazard. Mater.</source> <volume>483</volume>, <fpage>136541</fpage>. <pub-id pub-id-type="doi">10.1016/j.jhazmat.2024.136541</pub-id>
</citation>
</ref>
<ref id="B29">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Meenakshi</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Hiremath</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Meenakshi</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Shivaveerakumar</surname>
<given-names>S.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>Actinomycetes: isolation, cultivation and its active biomolecules</article-title>. <source>J. Pure Appl. Microbiol.</source> <volume>8</volume>, <fpage>118</fpage>&#x2013;<lpage>143</lpage>. <pub-id pub-id-type="doi">10.22207/jpam.18.1.48</pub-id>
</citation>
</ref>
<ref id="B30">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Mishra</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Lin</surname>
<given-names>Z.</given-names>
</name>
<name>
<surname>Pang</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Bhatt</surname>
<given-names>P.</given-names>
</name>
<name>
<surname>Chen</surname>
<given-names>S.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Recent advanced technologies for the characterization of xenobiotic-degrading microorganisms and microbial communities</article-title>. <source>Front. Bioeng. Biotechnol.</source> <volume>9</volume>, <fpage>632059</fpage>. <pub-id pub-id-type="doi">10.3389/fbioe.2021.632059</pub-id>
</citation>
</ref>
<ref id="B31">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Mishra</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Singh</surname>
<given-names>S. N.</given-names>
</name>
</person-group> (<year>2012</year>). <article-title>Microbial degradation of <italic>n</italic>-hexadecane in mineral salt medium as mediated by degradative enzymes</article-title>. <source>Bioresour. Technol.</source> <volume>111</volume>, <fpage>148</fpage>&#x2013;<lpage>154</lpage>. <pub-id pub-id-type="doi">10.1016/j.biortech.2012.02.049</pub-id>
</citation>
</ref>
<ref id="B32">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Mrunalini</surname>
<given-names>B. R.</given-names>
</name>
<name>
<surname>Girisha</surname>
<given-names>S. T.</given-names>
</name>
</person-group> (<year>2017</year>). <article-title>Screening and characterization of lipid inclusions in bacteria by fluorescence microscopy and mass spectrometry as a source for biofuel production</article-title>. <source>Indian J. Sci. Technol.</source> <volume>10</volume>, <fpage>1</fpage>&#x2013;<lpage>10</lpage>. <pub-id pub-id-type="doi">10.17485/ijst/2017/v10i21/111382</pub-id>
</citation>
</ref>
<ref id="B33">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Pal</surname>
<given-names>P.</given-names>
</name>
</person-group> (<year>2017</year>). <article-title>Treatment and disposal of pharmaceutical wastewater: toward the sustainable strategy</article-title>. <source>Sep. Purif. Rev.</source> <volume>47</volume>, <fpage>179</fpage>&#x2013;<lpage>198</lpage>. <pub-id pub-id-type="doi">10.1080/15422119.2017.1354888</pub-id>
</citation>
</ref>
<ref id="B34">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Payanthoth</surname>
<given-names>N. S.</given-names>
</name>
<name>
<surname>Mut</surname>
<given-names>N. N.</given-names>
</name>
<name>
<surname>Samanta</surname>
<given-names>P.</given-names>
</name>
<name>
<surname>Li</surname>
<given-names>G.</given-names>
</name>
<name>
<surname>Jung</surname>
<given-names>J.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>A review of biodegradation and formation of biodegradable microplastics in soil and freshwater environments</article-title>. <source>Appl. Biol. Chem.</source> <volume>67</volume>, <fpage>110</fpage>. <pub-id pub-id-type="doi">10.1186/s13765-024-00959-7</pub-id>
</citation>
</ref>
<ref id="B35">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Prasad</surname>
<given-names>G. S.</given-names>
</name>
<name>
<surname>Rao</surname>
<given-names>K. N.</given-names>
</name>
<name>
<surname>Girisham</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Reddy</surname>
<given-names>S. M.</given-names>
</name>
</person-group> (<year>2009</year>). <article-title>Bioconversion of meloxicam by bacteria</article-title>. <source>Afr. J. Biotechnol.</source> <volume>8</volume>, <fpage>3610</fpage>&#x2013;<lpage>3614</lpage>.</citation>
</ref>
<ref id="B36">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Prasad</surname>
<given-names>G. S.</given-names>
</name>
<name>
<surname>Rao</surname>
<given-names>K. N.</given-names>
</name>
<name>
<surname>Preethi</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Girisham</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Reddy</surname>
<given-names>S. M.</given-names>
</name>
</person-group> (<year>2011</year>). <article-title>Biotransformation of meloxicam by <italic>Cunninghamella blakesleeana</italic>: significance of carbon and nitrogen source</article-title>. <source>Indian J. Microbiol.</source> <volume>51</volume>, <fpage>82</fpage>&#x2013;<lpage>87</lpage>. <pub-id pub-id-type="doi">10.1007/s12088-011-0099-0</pub-id>
</citation>
</ref>
<ref id="B37">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Punchenko</surname>
<given-names>O. E.</given-names>
</name>
<name>
<surname>Punchenko</surname>
<given-names>E. V.</given-names>
</name>
<name>
<surname>Gostev</surname>
<given-names>V. V.</given-names>
</name>
<name>
<surname>Savchenko</surname>
<given-names>M. V.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>Study of bacterial susceptibility to antibiotic and phage combinations: a literature review</article-title>. <source>J. Microbiol. Epidemiol. Immunobiol.</source> <volume>101</volume>, <fpage>699</fpage>&#x2013;<lpage>705</lpage>. <pub-id pub-id-type="doi">10.36233/0372-9311-581</pub-id>
</citation>
</ref>
<ref id="B38">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Ram&#xed;rez</surname>
<given-names>G. J. R.</given-names>
</name>
<name>
<surname>Mu&#xf1;oz</surname>
<given-names>I. L. A.</given-names>
</name>
<name>
<surname>Balagurusamy</surname>
<given-names>N.</given-names>
</name>
<name>
<surname>Ram&#xed;rez</surname>
<given-names>F. J. E.</given-names>
</name>
<name>
<surname>Hern&#xe1;ndez</surname>
<given-names>A. L.</given-names>
</name>
<name>
<surname>Campos</surname>
<given-names>C. J.</given-names>
</name>
</person-group> (<year>2023</year>). <article-title>Microbiology and biochemistry of pesticides biodegradation</article-title>. <source>Int. J. Mol. Sci.</source> <volume>24</volume>, <fpage>15969</fpage>. <pub-id pub-id-type="doi">10.3390/ijms242115969</pub-id>
</citation>
</ref>
<ref id="B39">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Saeed</surname>
<given-names>H.</given-names>
</name>
<name>
<surname>Padmesh</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Singh</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Nandy</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Singh</surname>
<given-names>S. P.</given-names>
</name>
<name>
<surname>Deshwal</surname>
<given-names>R. K.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>Impact of veterinary pharmaceuticals on environment and their mitigation through microbial bioremediation</article-title>. <source>Front. Microbiol.</source> <volume>15</volume>, <fpage>1396116</fpage>. <pub-id pub-id-type="doi">10.3389/fmicb.2024.1396116</pub-id>
</citation>
</ref>
<ref id="B40">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Salina</surname>
<given-names>E. G.</given-names>
</name>
<name>
<surname>Martini</surname>
<given-names>B. A.</given-names>
</name>
<name>
<surname>Sorokin</surname>
<given-names>V. V.</given-names>
</name>
<name>
<surname>Mulyukin</surname>
<given-names>A. L.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>Fate of <italic>in vitro</italic> cultured <italic>Mycobacterium abscessus</italic> populations when exposed to moxifloxacin</article-title>. <source>Front. Microbiol.</source> <volume>15</volume>, <fpage>1494147</fpage>. <pub-id pub-id-type="doi">10.3389/fmicb.2024.1494147</pub-id>
</citation>
</ref>
<ref id="B41">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>S&#xe1;nchez-Su&#xe1;rez</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>D&#xed;az</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Coy-Barrera</surname>
<given-names>E.</given-names>
</name>
<name>
<surname>Villamil</surname>
<given-names>L.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Specialized metabolism of <italic>Gordonia</italic> genus: an integrated survey on chemodiversity combined with a comparative genomics-based analysis</article-title>. <source>BioTech</source> <volume>11</volume>, <fpage>53</fpage>. <pub-id pub-id-type="doi">10.3390/biotech11040053</pub-id>
</citation>
</ref>
<ref id="B42">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Shah</surname>
<given-names>B. A.</given-names>
</name>
<name>
<surname>Malhotra</surname>
<given-names>H.</given-names>
</name>
<name>
<surname>Papade</surname>
<given-names>S. E.</given-names>
</name>
<name>
<surname>Dhamale</surname>
<given-names>T.</given-names>
</name>
<name>
<surname>Ingale</surname>
<given-names>O. P.</given-names>
</name>
<name>
<surname>Kasarlawar</surname>
<given-names>S. T.</given-names>
</name>
<etal/>
</person-group> (<year>2024</year>). <article-title>Microbial degradation of contaminants of emerging concern: metabolic, genetic and omics insights for enhanced bioremediation</article-title>. <source>Front. Bioeng. Biotechnol.</source> <volume>12</volume>, <fpage>1470522</fpage>. <pub-id pub-id-type="doi">10.3389/fbioe.2024.1470522</pub-id>
</citation>
</ref>
<ref id="B43">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Shang</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Bai</surname>
<given-names>X.</given-names>
</name>
<name>
<surname>Chen</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Liu</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Li</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Xia</surname>
<given-names>X.</given-names>
</name>
<etal/>
</person-group> (<year>2019</year>). <article-title>Isolation and identification of a <italic>Bacillus megaterium</italic> strain with ochratoxin A removal ability and antifungal activity</article-title>. <source>Food Control</source> <volume>106</volume>, <fpage>106743</fpage>. <pub-id pub-id-type="doi">10.1016/j.foodcont.2019.106743</pub-id>
</citation>
</ref>
<ref id="B44">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Sheikhlangi</surname>
<given-names>Z.</given-names>
</name>
<name>
<surname>Gharaei</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Mirdar Harijani</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Davari</surname>
<given-names>S. A.</given-names>
</name>
<name>
<surname>Hassanein</surname>
<given-names>P.</given-names>
</name>
<name>
<surname>Rahdari</surname>
<given-names>A.</given-names>
</name>
</person-group> (<year>2023</year>). <article-title>Toxicological effects of meloxicam on physiological and antioxidant status of common carp (<italic>Cyprinus carpio</italic>)</article-title>. <source>Vet. Med. Sci.</source> <volume>9</volume>, <fpage>2085</fpage>&#x2013;<lpage>2094</lpage>. <pub-id pub-id-type="doi">10.1002/vms3.1207</pub-id>
</citation>
</ref>
<ref id="B45">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Singh</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Lalung</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Ivshina</surname>
<given-names>I.</given-names>
</name>
<name>
<surname>Kostova</surname>
<given-names>I.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>Editorial: Pharmaceutically active micropollutants &#x2013; how serious is the problem and is there a microbial way out?</article-title> <source>Front. Microbiol.</source> <volume>15</volume>, <fpage>1466334</fpage>. <pub-id pub-id-type="doi">10.3389/fmicb.2024.1466334</pub-id>
</citation>
</ref>
<ref id="B46">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Solomon</surname>
<given-names>E. I.</given-names>
</name>
<name>
<surname>Heppner</surname>
<given-names>D. E.</given-names>
</name>
<name>
<surname>Johnston</surname>
<given-names>E. M.</given-names>
</name>
<name>
<surname>Ginsbach</surname>
<given-names>J. W.</given-names>
</name>
<name>
<surname>Cirera</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Qayyum</surname>
<given-names>M.</given-names>
</name>
<etal/>
</person-group> (<year>2014</year>). <article-title>Copper active sites in biology</article-title>. <source>Chem. Rev.</source> <volume>114</volume>, <fpage>3659</fpage>&#x2013;<lpage>3853</lpage>. <pub-id pub-id-type="doi">10.1021/cr400327t</pub-id>
</citation>
</ref>
<ref id="B47">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Sowani</surname>
<given-names>H.</given-names>
</name>
<name>
<surname>Kulkarni</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Zinjarde</surname>
<given-names>S.</given-names>
</name>
</person-group> (<year>2017</year>). <article-title>An insight into the ecology, diversity and adaptations of <italic>Gordonia</italic> species</article-title>. <source>Crit. Rev. Microbiol.</source> <volume>44</volume> (<issue>1</issue>), <fpage>393</fpage>&#x2013;<lpage>413</lpage>. <pub-id pub-id-type="doi">10.1080/1040841X.2017.1418286</pub-id>
</citation>
</ref>
<ref id="B48">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>&#x15a;wiacka</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Michnowska</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Maculewicz</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Caban</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Smolarz</surname>
<given-names>K.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Toxic effects of NSAIDs in non-target species: A review from the perspective of the aquatic environment</article-title>. <source>Environ. Pollut.</source> <volume>273</volume>, <fpage>115891</fpage>. <pub-id pub-id-type="doi">10.1016/j.envpol.2020.115891</pub-id>
</citation>
</ref>
<ref id="B49">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Taheur</surname>
<given-names>B. F.</given-names>
</name>
<name>
<surname>Kouidhi</surname>
<given-names>B.</given-names>
</name>
<name>
<surname>Qurashi</surname>
<given-names>Y. M. A.</given-names>
</name>
<name>
<surname>Salah-Abb&#xe8;s</surname>
<given-names>B. J.</given-names>
</name>
<name>
<surname>Chaieb</surname>
<given-names>K.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>Review: Biotechnology of mycotoxins detoxification using microorganisms and enzymes</article-title>. <source>Toxicon</source> <volume>160</volume>, <fpage>12</fpage>&#x2013;<lpage>22</lpage>. <pub-id pub-id-type="doi">10.1016/j.toxicon.2019.02.001</pub-id>
</citation>
</ref>
<ref id="B50">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Tavares</surname>
<given-names>I. A.</given-names>
</name>
</person-group> (<year>2000</year>). <article-title>The effects of meloxicam, indomethacin or NS-398 on eicosanoid synthesis by fresh human gastric mucosa</article-title>. <source>Aliment. Pharmacol. Ther.</source> <volume>14</volume>, <fpage>795</fpage>&#x2013;<lpage>799</lpage>. <pub-id pub-id-type="doi">10.1046/j.1365-2036.2000.00760.x</pub-id>
</citation>
</ref>
<ref id="B51">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Ugalde</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>De Koning</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Wallraven</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Bruyneel</surname>
<given-names>B.</given-names>
</name>
<name>
<surname>Vermeulen</surname>
<given-names>N.</given-names>
</name>
<name>
<surname>Grossmann</surname>
<given-names>T.</given-names>
</name>
<etal/>
</person-group> (<year>2018</year>). <article-title>Linking cytochrome P450 enzymes from <italic>Mycobacterium tuberculosis</italic> to their cognate ferredoxin partners</article-title>. <source>Appl. Microbiol. Biotechnol.</source> <volume>102</volume>, <fpage>9231</fpage>&#x2013;<lpage>9242</lpage>. <pub-id pub-id-type="doi">10.1007/s00253-018-9299-4</pub-id>
</citation>
</ref>
<ref id="B52">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wang</surname>
<given-names>F.</given-names>
</name>
<name>
<surname>Xiang</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Leung</surname>
<given-names>K. S.-Y.</given-names>
</name>
<name>
<surname>Elsner</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Guo</surname>
<given-names>Y.</given-names>
</name>
<etal/>
</person-group> (<year>2024</year>). <article-title>Emerging contaminants: A one health perspective</article-title>. <source>Innovation</source> <volume>5</volume>, <fpage>100612</fpage>. <pub-id pub-id-type="doi">10.1016/j.xinn.2024.100612</pub-id>
</citation>
</ref>
<ref id="B53">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wang</surname>
<given-names>N.</given-names>
</name>
<name>
<surname>Sun</surname>
<given-names>H.</given-names>
</name>
<name>
<surname>Dong</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Ouyang</surname>
<given-names>D.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>PharmDE: A new expert system for drug-excipient compatibility evaluation</article-title>. <source>Int. J. Pharm.</source> <volume>607</volume>, <fpage>120962</fpage>. <pub-id pub-id-type="doi">10.1016/j.ijpharm.2021.120962</pub-id>
</citation>
</ref>
<ref id="B54">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wei</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Dhanasekaran</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Yang</surname>
<given-names>Q.</given-names>
</name>
<name>
<surname>Ngea</surname>
<given-names>G. L. N.</given-names>
</name>
<name>
<surname>Godana</surname>
<given-names>E. A.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>H.</given-names>
</name>
</person-group> (<year>2022</year>). <article-title>Degradation and stress response mechanism of <italic>Cryptococcus podzolicus</italic> Y3 on ochratoxin A at the transcriptional level</article-title>. <source>LWT</source> <volume>157</volume>, <fpage>113061</fpage>. <pub-id pub-id-type="doi">10.1016/j.lwt.2021.113061</pub-id>
</citation>
</ref>
<ref id="B55">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wiegand</surname>
<given-names>I.</given-names>
</name>
<name>
<surname>Hilpert</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Hancock</surname>
<given-names>R. E. W.</given-names>
</name>
</person-group> (<year>2008</year>). <article-title>Agar and broth dilution methods to determine the minimal inhibitory concentration (MIC) of antimicrobial substances</article-title>. <source>Nat. Protoc.</source> <volume>3</volume>, <fpage>163</fpage>&#x2013;<lpage>175</lpage>. <pub-id pub-id-type="doi">10.1038/nprot.2007.521</pub-id>
</citation>
</ref>
<ref id="B56">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wilkinson</surname>
<given-names>J. L.</given-names>
</name>
<name>
<surname>Thornhill</surname>
<given-names>I.</given-names>
</name>
<name>
<surname>Oldenkamp</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Gachanja</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Busquets</surname>
<given-names>R.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>Pharmaceuticals and personal care products in the aquatic environment: how can regions at risk be identified in the future?</article-title> <source>Environ. Toxicol. Chem.</source> <volume>43</volume>, <fpage>575</fpage>&#x2013;<lpage>588</lpage>. <pub-id pub-id-type="doi">10.1002/etc.5763</pub-id>
</citation>
</ref>
<ref id="B57">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wilson</surname>
<given-names>W. W.</given-names>
</name>
<name>
<surname>Wade</surname>
<given-names>M. M.</given-names>
</name>
<name>
<surname>Holman</surname>
<given-names>S. C.</given-names>
</name>
<name>
<surname>Champlin</surname>
<given-names>F. R.</given-names>
</name>
</person-group> (<year>2001</year>). <article-title>Status of methods for assessing bacterial cell surface charge properties based on zeta potential measurements</article-title>. <source>J. Microbiol. Methods</source> <volume>42</volume>, <fpage>153</fpage>&#x2013;<lpage>164</lpage>. <pub-id pub-id-type="doi">10.1016/S0167-7012(00)00224-4</pub-id>
</citation>
</ref>
<ref id="B58">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wu</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Wang</surname>
<given-names>F.</given-names>
</name>
<name>
<surname>Xia</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>Z.</given-names>
</name>
<name>
<surname>Wang</surname>
<given-names>Z.</given-names>
</name>
<name>
<surname>Wang</surname>
<given-names>K.</given-names>
</name>
<etal/>
</person-group> (<year>2022</year>). <article-title>Meta-analysis of the impacts of phosphorus addition on soil microbes</article-title>. <source>Agr. Ecosyst. Environ.</source> <volume>340</volume>, <fpage>108180</fpage>. <pub-id pub-id-type="doi">10.1016/j.agee.2022.108180</pub-id>
</citation>
</ref>
<ref id="B59">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Xia</surname>
<given-names>X.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Li</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Garba</surname>
<given-names>B.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>Q.</given-names>
</name>
<name>
<surname>Wang</surname>
<given-names>Y.</given-names>
</name>
<etal/>
</person-group> (<year>2017</year>). <article-title>Isolation and characterization of a <italic>Bacillus subtilis</italic> strain with aflatoxin B1 biodegradation capability</article-title>. <source>Food Control</source> <volume>75</volume>, <fpage>92</fpage>&#x2013;<lpage>98</lpage>. <pub-id pub-id-type="doi">10.1016/j.foodcont.2016.12.036</pub-id>
</citation>
</ref>
<ref id="B60">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Xu</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Wang</surname>
<given-names>X. F.</given-names>
</name>
<name>
<surname>Liu</surname>
<given-names>B.</given-names>
</name>
<name>
<surname>Sun</surname>
<given-names>T.</given-names>
</name>
<name>
<surname>Wang</surname>
<given-names>X.</given-names>
</name>
</person-group> (<year>2021</year>). <article-title>Fabrication of ferrous tungstate with enhanced sonocatalytic performance for meloxicam removal</article-title>. <source>Coll. Surf. A</source> <volume>627</volume>, <fpage>127222</fpage>. <pub-id pub-id-type="doi">10.1016/j.colsurfa.2021.127222</pub-id>
</citation>
</ref>
<ref id="B61">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Yan</surname>
<given-names>H.</given-names>
</name>
<name>
<surname>Xu</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Su</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Wei</surname>
<given-names>H.</given-names>
</name>
<name>
<surname>Li</surname>
<given-names>X.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>Synergistic promotion of sludge reduction by surfactant-producing and lysozyme-producing bacteria: Optimization and effect of Na<sup>&#x2b;</sup>
</article-title>. <source>Bioresour. Technol.</source> <volume>393</volume>, <fpage>130065</fpage>. <pub-id pub-id-type="doi">10.1016/j.biortech.2023.130065</pub-id>
</citation>
</ref>
<ref id="B62">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhang</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Yang</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Ding</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Wang</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Lan</surname>
<given-names>L.</given-names>
</name>
<name>
<surname>Ma</surname>
<given-names>Q.</given-names>
</name>
<etal/>
</person-group> (<year>2017</year>). <article-title>Bacterial lipid droplets bind to DNA via an intermediary protein that enhances survival under stress</article-title>. <source>Nat. Commun.</source> <volume>8</volume>, <fpage>15979</fpage>. <pub-id pub-id-type="doi">10.1038/ncomms15979</pub-id>
</citation>
</ref>
<ref id="B63">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhang</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Zhao</surname>
<given-names>Q.</given-names>
</name>
<name>
<surname>Ngea</surname>
<given-names>G. L. N.</given-names>
</name>
<name>
<surname>Godana</surname>
<given-names>E. A.</given-names>
</name>
<name>
<surname>Yang</surname>
<given-names>Q.</given-names>
</name>
<name>
<surname>Zhang</surname>
<given-names>H.</given-names>
</name>
</person-group> (<year>2024</year>). <article-title>Biodegradation of patulin in fresh pear juice by an aldo-keto reductase from <italic>Meyerozyma guilliermondii</italic>
</article-title>. <source>Food Chem.</source> <volume>15</volume>, <fpage>137696</fpage>. <pub-id pub-id-type="doi">10.1016/j.foodchem.2023.137696</pub-id>
</citation>
</ref>
<ref id="B64">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zhou</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Di Paolo</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Wu</surname>
<given-names>X.</given-names>
</name>
<name>
<surname>Shao</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Seiler</surname>
<given-names>T. B.</given-names>
</name>
<name>
<surname>Hollert</surname>
<given-names>H.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>Optimization of screening-level risk assessment and priority selection of emerging pollutants &#x2013; The case of pharmaceuticals in European surface waters</article-title>. <source>Environ. Int.</source> <volume>128</volume>, <fpage>1</fpage>&#x2013;<lpage>10</lpage>. <pub-id pub-id-type="doi">10.1016/j.envint.2019.04.034</pub-id>
</citation>
</ref>
<ref id="B65">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Zorrilla</surname>
<given-names>I.</given-names>
</name>
<name>
<surname>Martinez</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Taggart</surname>
<given-names>M. A.</given-names>
</name>
<name>
<surname>Richards</surname>
<given-names>N.</given-names>
</name>
</person-group> (<year>2015</year>). <article-title>Suspected flunixin poisoning of a wild Eurasian Griffon Vulture from Spain</article-title>. <source>Conserv. Biol.</source> <volume>29</volume>, <fpage>587</fpage>&#x2013;<lpage>592</lpage>. <pub-id pub-id-type="doi">10.1111/cobi.12417</pub-id>
</citation>
</ref>
</ref-list>
</back>
</article>