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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Microbiol.</journal-id>
<journal-title>Frontiers in Microbiology</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Microbiol.</abbrev-journal-title>
<issn pub-type="epub">1664-302X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fmicb.2022.930357</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Microbiology</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Antibiotic-Induced Changes in Pigment Accumulation, Photosystem II, and Membrane Permeability in a Model Cyanobacterium</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name><surname>Yalcin</surname> <given-names>Yavuz S.</given-names></name>
</contrib>
<contrib contrib-type="author">
<name><surname>Aydin</surname> <given-names>Busra N.</given-names></name>
</contrib>
<contrib contrib-type="author">
<name><surname>Sayadujjhara</surname> <given-names>Mst</given-names></name>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name><surname>Sitther</surname> <given-names>Viji</given-names></name>
<xref ref-type="corresp" rid="c001"><sup>&#x002A;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1759441/overview"/>
</contrib>
</contrib-group>
<aff><institution>Department of Biology, Morgan State University</institution>, <addr-line>Baltimore, MD</addr-line>, <country>United States</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Ajay Kumar, Department of Postharvest Science of Fresh Produce, Agricultural Research Organization (ARO), Israel</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Ashwani Rai, Banaras Hindu University, India; Prashant Kumar Singh, Pachhunga University College, India</p></fn>
<corresp id="c001">&#x002A;Correspondence: Viji Sitther, <email>viji.sitther@morgan.edu</email></corresp>
<fn fn-type="other" id="fn004"><p>This article was submitted to Microbiotechnology, a section of the journal Frontiers in Microbiology</p></fn>
</author-notes>
<pub-date pub-type="epub">
<day>22</day>
<month>06</month>
<year>2022</year>
</pub-date>
<pub-date pub-type="collection">
<year>2022</year>
</pub-date>
<volume>13</volume>
<elocation-id>930357</elocation-id>
<history>
<date date-type="received">
<day>27</day>
<month>04</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>25</day>
<month>05</month>
<year>2022</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2022 Yalcin, Aydin, Sayadujjhara and Sitther.</copyright-statement>
<copyright-year>2022</copyright-year>
<copyright-holder>Yalcin, Aydin, Sayadujjhara and Sitther</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>
<p><italic>Fremyella diplosiphon</italic> is a well-studied a model cyanobacterium for photosynthesis due to its efficient light absorption potential and pigment accumulation. In the present study, the impact of ampicillin, tetracycline, kanamycin, and cefotaxime on pigment fluorescence and photosynthetic capacity in <italic>Fremyella diplosiphon</italic> strains B481-WT and B481-SD was investigated. Our results indicated that both strains exposed to kanamycin from 0.2 to 3.2 mg/L and tetracycline from 0.8 to 12.8 mg/L enhanced growth and pigment accumulation. Additionally, B481-SD treated with 0.2&#x2013;51.2 mg/L ampicillin resulted in a significant enhancement of pigment fluorescence. A detrimental effect on growth and pigmentation in both the strains exposed to 6.4&#x2013;102.5 mg/L kanamycin and 0.8&#x2013;102.5 mg/L cefotaxime was observed. Detection of reactive oxygen species revealed highest levels of oxidative stress at 51.2 and 102.5 mg/L kanamycin for B481-<italic>SD</italic> and 102.5 mg/L for B481-WT. Membrane permeability detected by lactate dehydrogenase assay indicated maximal activity at 0.8 mg/L ampicillin, kanamycin, and tetracycline treatments on day 6. Abundant vacuolation, pyrophosphate, and cyanophycin granule formation were observed in treated cells as a response to antibiotic stress. These findings on the hormetic effect of antibiotics on <italic>F. diplosiphon</italic> indicate that optimal antibiotic concentrations induce cellular growth while high concentrations severely impact cellular functionality. Future studies will be aimed to enhance cellular lipid productivity at optimal antibiotic concentrations to disintegrate the cell wall, thus paving the way for clean bioenergy applications.</p>
</abstract>
<kwd-group>
<kwd>cyanobacteria</kwd>
<kwd>fluorescence yield</kwd>
<kwd><italic>Fremyella diplosiphon</italic></kwd>
<kwd>hormetic effect</kwd>
<kwd>lactate dehydrogenase</kwd>
<kwd>oxidative stress</kwd>
<kwd>&#x03B2;-lactams</kwd>
</kwd-group>
<counts>
<fig-count count="6"/>
<table-count count="0"/>
<equation-count count="0"/>
<ref-count count="39"/>
<page-count count="9"/>
<word-count count="5231"/>
</counts>
</article-meta>
</front>
<body>
<sec id="S1" sec-type="intro">
<title>Introduction</title>
<p>In recent years, increased antibiotic contamination in surface and groundwater has drawn worldwide attention due to their potential consequences for the environmental ecosystem and health. Globally, antibiotic consumption has increased by 64% and at the rate of 39% over the past two decades (<xref ref-type="bibr" rid="B38">WHO, 2016</xref>; <xref ref-type="bibr" rid="B6">Browne et al., 2021</xref>). In the United States alone, about 10,000 tons per annum of antibiotics are consumed and account for &#x223C;70% of the nation&#x2019;s annual antimicrobial consumption (<xref ref-type="bibr" rid="B35">U.S. Food and Drug Administration, 2019</xref>). Antibiotic residues excreted in urine and feces after metabolism are directly introduced to the aquatic environments by poorly managed livestock that have direct access to surface water or indirectly by animal manure (<xref ref-type="bibr" rid="B20">K&#x00FC;mmerer, 2009</xref>; <xref ref-type="bibr" rid="B3">Bailey et al., 2015</xref>; <xref ref-type="bibr" rid="B27">Pan et al., 2021</xref>). While non-targeted antibiotic exposure on eukaryotes is minimal compared to prokaryotes, cyanobacteria are ten times more sensitive than algae to the harmful effects of antibiotics because of fragile cell structures (<xref ref-type="bibr" rid="B25">Norvill et al., 2016</xref>; <xref ref-type="bibr" rid="B19">Kulkarni et al., 2017</xref>). About 20 different kinds of antibiotics have been detected in the range of 1.26&#x2013;127.49 ng/L in various aquatic environments (<xref ref-type="bibr" rid="B17">Kim et al., 2018</xref>). Of these, the &#x03B2;-lactam group, primarily the penicillin and cephalosporins, constitutes 50&#x2013;60% of the most consumed antibiotics (<xref ref-type="bibr" rid="B16">Kapoor et al., 2017</xref>). Significant amount of &#x03B2;-lactams are directly excreted without any structural changes after metabolism (<xref ref-type="bibr" rid="B32">Snow et al., 2009</xref>). Besides, antibiotic residues are detrimental to microbial communities in aquatic ecosystems and are known to greatly impact cellular metabolism in cyanobacteria (<xref ref-type="bibr" rid="B14">Gonz&#x00E1;lez-Pleiter et al., 2013</xref>; <xref ref-type="bibr" rid="B9">Cui et al., 2020</xref>). The hormesis phenomenon (biphasic effect) in response to harmful environmental agents by low-dose stimulation and high-dose inhibition has been extensively studied (<xref ref-type="bibr" rid="B18">Kouda and Iki, 2010</xref>). Exposure of <italic>Microcystis aeruginosa</italic>to low dosages (&#x003C; 20 mg/L) of erythromycin has been reported to trigger photosynthetic activity <italic>(Fv/Fm)</italic> (<xref ref-type="bibr" rid="B39">Wu et al., 2020</xref>).</p>
<p>Of the various cyanobacterial strains, <italic>Fremyella diplosiphon</italic> is a widely studied model organism known for its adaptive growth capability in varying light intensities. Besides, its ability to produce lipids and desirable essential fatty acids make it an ideal third generation biofuel agent. To our knowledge, the impact of antibiotics on <italic>F. diplosiphon</italic> growth and cell membrane permeability remains unknown. In this study, the impact of ampicillin, tetracycline, kanamycin, and cefotaxime on pigment accumulation, photosystem II (PSII) activity, reactive oxygen species (ROS) formation, and cell membrane permeability in <italic>F. diplosiphon</italic> strains B481-SD and B481-WT was investigated. Morphological alterations in cells exposed to antibiotics were observed by microscopic examinations.</p>
</sec>
<sec id="S2" sec-type="materials|methods">
<title>Materials and Methods</title>
<sec id="S2.SS1">
<title>Cyanobacterial Strains and Growth Conditions</title>
<p><italic>F. diplosiphon</italic> strains, B481-WT obtained from the UTEX algae repository (Austin, TX, United States), and B481-SD (overexpressed strain with the sterol desaturase gene; accession <ext-link ext-link-type="DDBJ/EMBL/GenBank" xlink:href="MH329183">MH329183</ext-link>) were used in this study. Cultures were grown in liquid BG-11/HEPES medium under wide-spectrum red light (650 nm) with continuous shaking at 170 rpm at 28&#x00B0;C in an Innova 44R shaker (Eppendorf, Hamburg, Germany) for 6 days. Light fluence rate was adjusted to 30 &#x03BC;mol m<sup>&#x2013;2</sup> s <sup>&#x2013;1</sup> using the model LI-190SA quantum sensor (Li-Cor, United States). These conditions were kept constant during the study.</p>
</sec>
<sec id="S2.SS2">
<title>Antibiotic Treatment</title>
<p>Three classes of antibiotics: &#x03B2;-lactams (ampicillin, cefotaxime), aminoglycosides (kanamycin), and tetracycline, were tested in this study. Antibiotic stock solutions (25x&#x2013;100x) were prepared according to the manufacturer&#x2019;s instructions and stored at -20&#x00B0;C. Working solutions in the range of 0.2&#x2013;102.5 mg/L for ampicillin, kanamycin, cefotaxime and 410 mg/L for tetracycline were used in this study (<xref ref-type="bibr" rid="B11">Dias et al., 2015</xref>; <xref ref-type="bibr" rid="B31">Shang et al., 2015</xref>). Ampicillin, cefotaxime, and kanamycin working solutions were prepared immediately before use and diluted in ddH<sub>2</sub>O to the desired concentrations (<xref ref-type="bibr" rid="B4">Baselga-Cervera et al., 2019</xref>). Each antibiotic concentration was mixed with 5 ml <italic>F. diplosiphon</italic> cells adjusted to OD750 nm. Assays were performed in 96-well clear polystyrene microplate (Corning<sup>&#x00AE;</sup>Inc., NY) and cultures grown under conditions mentioned above. Three replicate treatments were maintained and the experiment was repeated twice. In order to minimize the effects of light scattering, every other well was left blank. Plates were sealed with a Breathe-Easy sealing membrane (Sigma-Aldrich, MO, Lot#MKCP8263) to prevent evaporative water loss and decrease the risk of contamination.</p>
</sec>
<sec id="S2.SS3">
<title>Pigment and Photosynthesis Analysis in Antibiotic-Treated <italic>Fremyella diplosiphon</italic></title>
<p>Phycocyanin and chlorophyll <italic>a</italic> fluorescence in antibiotic-treated and control <italic>F. diplosiphon</italic> were recorded every other day using a microplate reader (BioTek Synergy H1 Microplate Reader, Agilent, United States). While chlorophyll <italic>a</italic> fluorescence was recorded at an excitation of 420 nm and emission of 680 nm, phycocyanin was measured at an excitation of 590 nm and emissions of 650 nm (<xref ref-type="bibr" rid="B28">Roha&#x00EC;&#x010D;ek and Barta&#x00EC;k, 1999</xref>). Fluorescence Epi-RGB mode was used for macro evaluation in 96 well plates on day 6 (Amersham Imager 680, GE Healthcare Bio-Sciences AB, Uppsala, Sweden). Minimal and maximal fluorescence yield (<italic>Fo</italic> and <italic>Fm</italic>) was measured using MINI-PAM (Walz, Effeltrich, Germany) every 48 h for 6 days after incubation in dark for 15 min. Based on these parameters PSII quantum yield (<italic>Fv/Fo</italic>) was calculated using the equation <italic>Fv</italic>/<italic>Fo</italic> = (<italic>Fm</italic>&#x2212;<italic>Fo</italic>)/<italic>Fo</italic> (<xref ref-type="bibr" rid="B36">Wan et al., 2015</xref>).</p>
</sec>
<sec id="S2.SS4">
<title>Reactive Oxygen Species Assay</title>
<p>Oxidative stress in antibiotic-treated <italic>F. diplosiphon</italic> strains was detected using 2&#x2019;,7&#x2019;-dichlorofluorescein diacetate, also known as H<sub>2</sub>DCFDA (EMD Chemicals, United States) (<xref ref-type="bibr" rid="B1">Ajiboye et al., 2017</xref>). After growth of cells in varying antibiotic concentrations for 6 days under conditions mentioned above, a fresh 20 mM DCFDA stock was prepared, and 50 &#x03BC;L added to 150 &#x03BC;l cells in a 96 well plate (<xref ref-type="bibr" rid="B7">Busch and Montgomery, 2015</xref>). Fluorescence intensity was measured at an excitation of 529 nm and emission of 495 nm using a microplate reader after incubation in the dark for 45 min at room temperature (BioTek Synergy H1 Microplate Reader, Agilent, United States). Three replicate treatments were maintained and the experiment repeated once.</p>
</sec>
<sec id="S2.SS5">
<title>Lactate Dehydrogenase Assay and Microscopic Observations</title>
<p>The toxicity of ampicillin, tetracycline, and kanamycin on <italic>F. diplosiphon</italic> was assessed using the Pierce&#x2122; (LDH Cytotoxicity Assay Kit, Thermo Fisher Scientific, United States) according to the manufacturer&#x2019;s protocol. Since cefotaxime resulted in cell death on day 6, it was not included for this assay. Strains B481-WT and B481-SD were grown in liquid BG-11/HEPES medium containing 0.2&#x2013;102.5 mg/L ampicillin, tetracycline, and kanamycin in 10 ml vented culture flasks. Cells at an optical density of 0.2 at OD750 nm were grown under continuous shaking at 70 rpm and 30 &#x03BC;mol m<sup>&#x2013;2</sup> s<sup>&#x2013;1</sup> at 28&#x00B0;C in an Innova 44R shaker. Cells grown in the absence of antibiotics served as control. The flasks were placed in an incubator at 37&#x00B0;C in the dark for 24 h prior to LDH measurement. On day 6, 50 &#x03BC;l cultures were transferred to a 96 well plate, and 50 &#x03BC;L of the reaction mixture (LDH Cytotoxicity Assay Kit, Thermo Fisher Scientific, United States) was added. After incubation for 30 min. at room temperature in the dark, 50 &#x03BC;L of stop solution was added and mixed gently (<xref ref-type="bibr" rid="B37">Wejnerowski et al., 2018</xref>). Absorbance was measured at 490 nm using a microplate reader (BioTek Synergy H1 Microplate Reader, Agilent, United States) after 2 h incubation in the dark at room temperature. Three replicates per treatment were maintained and the experiment was repeated. On day 6, microscopic observations were made using a cytation 5 Cell Imaging Multi-Mode reader (BioTek<sup>&#x00AE;</sup> Instruments, Inc., Winooski, United States).</p>
</sec>
<sec id="S2.SS6">
<title>Statistical Analysis</title>
<p>Repeated ANOVA and Tukey&#x2019;s multiple comparison tests including Pearson&#x2019;s correlation were used to analyze <italic>F. diplosiphon</italic> sensitivity to different antibiotic treatments at each sampling point. SPSS 28.0 (IBM Corporation, Armonk, United States) was also used to analyze and plot the data.</p>
</sec>
</sec>
<sec id="S3" sec-type="results">
<title>Results</title>
<sec id="S3.SS1">
<title>Antibiotics Impact Pigment Fluorescence in <italic>Fremyella diplosiphon</italic> Strains</title>
<p>Phycocyanin and chlorophyll <italic>a</italic> pigment autofluorescence was quantified to evaluate the effect of antibiotics on <italic>F. diplosiphon</italic> growth. Strain B481-SD treated with ampicillin ranging from 0.2 to 25.6 mg/L exhibited significant increases in phycocyanin and chlorophyll <italic>a</italic> autofluorescence; however, a significant decrease was detected at 51.2 and 102.5 mg/L (<italic>p</italic> &#x003C; 0.01) (<xref ref-type="fig" rid="F1">Figures 1A</xref>, <xref ref-type="fig" rid="F2">2A</xref>). By contrast, B481-WT treated with ampicillin exhibited a significant decrease in pigment autofluorescence from 3.2 to 102.5 mg/L compared to the untreated control. We observed a significant reduction of pigment autofluorescence in B481-SD and B481-WT treated with cefotaxime ranging from 0.8 to 102.5 mg/L and 0.2 to 102.5 mg/L respectively (<xref ref-type="fig" rid="F1">Figures 1B,F</xref>, <xref ref-type="fig" rid="F2">2B,F</xref>). A significant reduction in phycocyanin and chlorophyll <italic>a</italic> autofluorescence was observed in both strains exposed to kanamycin from 6.4 to 102.5 mg/L when compared to the untreated control. However, a significant increase in B481-SD autofluorescence at lower kanamycin concentrations of 0.2&#x2013;3.2 mg/L when compared to the control was observed (<xref ref-type="fig" rid="F1">Figures 1C</xref>, <xref ref-type="fig" rid="F2">2C</xref>). B481-SD treated with tetracycline reduced phycocyanin and chlorophyll <italic>a</italic> autofluorescence at concentrations ranging from 102.5 to 410 mg/L, while it ranged from 25.6 to 410 mg/L for B481-WT. A significant increase in pigment autofluorescence was observed in both strains treated with tetracycline from 0.8 to 12.8 mg/L on day 6 (<xref ref-type="fig" rid="F1">Figures 1D,H</xref>, <xref ref-type="fig" rid="F2">2D,H</xref>).</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption><p>Phycocyanin autofluorescense of B481-SD and B481-WT strains reflected by 590 nm excitation and 650 nm emission. B481-SD strain was exposed to concentrations ranging from 0.2 to 102.5 mg/L ampicillin, cefotaxime, kanamycin, and tetracycline <bold>(A&#x2013;D)</bold>, and B481-WT strain to ampicillin and kanamycin concentrations ranging from 0.2 to 102.5 mg/L; 0.05&#x2013;102.5 mg/L for cefotaxime and 0.2&#x2013;410 mg/L for tetracycline <bold>(E&#x2013;H)</bold>. Both strains were cultivated in antibiotics for 6 days at 28&#x00B0;C with a light intensity of 30 &#x03BC;mol m<sup>&#x2013; 2</sup> s<sup>&#x2013;1</sup>. Mean and standard deviations are indicated by error bars.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmicb-13-930357-g001.tif"/>
</fig>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption><p>Chlorophyll <italic>a</italic> autofluorescence of <italic>Fremyella diplosiphon</italic> strains B481-SD and B481-WT reflected by excitation of 420 nm and emission of 680 nm. B481-SD strain was exposed to ampicillin, cefotaxime, kanamycin, and tetracycline concentrations ranging from 0.2 to 102.5 mg/L <bold>(A&#x2013;D)</bold>, B481-WT strain was exposed to ampicillin and kanamycin concentrations ranging from 0.2 to 102.5 mg/L; 0.05&#x2013;102.5 mg/L for cefotaxime and 0.2&#x2013;410 mg/L for tetracycline <bold>(E&#x2013;H)</bold>. Both strains are cultivated with four antibiotics for 6 days at 28&#x00B0;C with a light intensity of 30 &#x03BC;mol m<sup>&#x2013;2</sup> s<sup>&#x2013;1</sup>. Mean and standard deviations are indicated by error bars.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmicb-13-930357-g002.tif"/>
</fig>
</sec>
<sec id="S3.SS2">
<title>Photosynthetic Efficacy of <italic>Fremyella diplosiphon</italic> Exposed to Varying Antibiotic Concentrations</title>
<p>Quantification of photosynthetic efficiency (<italic>Fv/Fo</italic>) revealed a significant increase in B481-SD strain treated with ampicillin at 0.2&#x2013;3.2 mg/L on day 4 compared to the control (<xref ref-type="fig" rid="F3">Figure 3A</xref>). On the other hand, a significant reduction of <italic>Fv/Fo</italic> ratios was observed in B-481-SD treated with 51.2 and 102.8 mg/L ampicillin on day 6 (<xref ref-type="fig" rid="F3">Figures 3A,B</xref>). A substantial reduction in the <italic>Fv/Fo</italic> ratios in cefotaxime-treated cells was observed, with no recovery of B481-SD and B481-WT at concentrations higher than 1.6 mg/L and 0.05 mg/L respectively (<xref ref-type="fig" rid="F3">Figures 3C,D</xref>). While we observed a significant decrease in <italic>Fv/Fo</italic> ratio in both strains treated with kanamycin from 1.6 to 102.5 mg/L, a significant increase in B481-WT at concentrations ranging from 0.2 to 1.6 mg/L kanamycin compared with the control group was noted (<xref ref-type="fig" rid="F3">Figure 3F</xref>). We also observed a decrease in <italic>Fv/Fo</italic> ratios in both strains exposed to tetracycline concentrations higher than 102.5 mg/L (<italic>p</italic> &#x003C; 0.05) (<xref ref-type="fig" rid="F3">Figures 3G,H</xref>).</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption><p>Variance of <italic>Fv/Fo</italic> in B481-SD <bold>(A,C,E,G)</bold> and B481-WT <bold>(B,D,F,H)</bold> strains of <italic>Fremyella diplosiphon</italic> in response to ampicillin, cefotaxime, kanamycin, and tetracycline exposure for 6 days. Mean and standard deviations are indicated by error bars.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmicb-13-930357-g003.tif"/>
</fig>
</sec>
<sec id="S3.SS3">
<title>Detection of Reactive Oxygen Species in Antibiotic-Treated <italic>Fremyella diplosiphon</italic></title>
<p>Antibiotic-induced ROS measured using the dichlorodihydrofluorescein revealed significantly higher levels (<italic>p</italic> &#x003C; 0.01) in both strains treated with cefotaxime, kanamycin, and tetracycline from 0.2 to 102.5 mg/L compared to the untreated control (<xref ref-type="fig" rid="F4">Figures 4A,B</xref>). While B481-SD treated with 102.5 mg/L ampicillin exhibited significantly higher ROS (<italic>p</italic> &#x003C; 0.01), it ranged from 6.4 to 102.5 mg/L for B481-WT (<xref ref-type="fig" rid="F4">Figures 4A,B</xref>). Highest levels of oxidative stress were observed at 51.2 and 102.5 mg/L kanamycin for B481-SD and 102.5 mg/L for B-481-WT.</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption><p>Reactive oxygen species generated in B481-SD <bold>(A)</bold> and B481-WT <bold>(B)</bold> <italic>Fremyella diplosiphon</italic> strains exposed to ampicillin, cefotaxime, kanamycin, and tetracycline. Mean and standard deviations are indicated by error bars.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmicb-13-930357-g004.tif"/>
</fig>
</sec>
<sec id="S3.SS4">
<title>Membrane Integrity in Antibiotic-Treated <italic>Fremyella diplosiphon</italic></title>
<p>B481-SD and B481-WT strains treated with ampicillin, tetracycline, and kanamycin exhibited maximum LDH activity at the concentrations of 0.8 and 0.4 mg/L. Specifically, enhanced LDH activity (<italic>p</italic> &#x003C; 0.05) was observed in B481-SD treated with tetracycline, ampicillin, and kanamycin from 0.2 to 0.8 mg/L (<xref ref-type="fig" rid="F5">Figure 5A</xref>). The LDH activity of B481-WT was higher in kanamycin and tetracycline at 0.4 mg/L compared to ampicillin at the same concentration (<xref ref-type="fig" rid="F5">Figure 5B</xref>). Microscopic observations such as filament fragmentation and alteration of cell shape were observed at concentrations higher than 25.6 mg/L ampicillin for B481-WT and 51.2 mg/L kanamycin for B481-SD and B481-WT (<xref ref-type="fig" rid="F6">Figures 6B&#x2013;D</xref>). In addition, cellular stress-related structures such as pyrophosphate granules (<xref ref-type="fig" rid="F6">Figure 6F</xref>, green rectangle), akinetes (<xref ref-type="fig" rid="F6">Figure 6A</xref>, yellow arrows), and cellular vacuoles (<xref ref-type="fig" rid="F6">Figures 6B&#x2013;F</xref>, red arrows) were observed in the strains exposed to higher antibiotic concentrations.</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption><p>Lactate dehydrogenase activity in B481-SD and B481-WT strains of <italic>Fremyella diplosiphon</italic> exposed to varying concentrations of ampicillin, kanamycin, and tetracycline <bold>(A,B)</bold> on day 6. Mean and standard deviations are indicated by error bars.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmicb-13-930357-g005.tif"/>
</fig>
<fig id="F6" position="float">
<label>FIGURE 6</label>
<caption><p>Morphological alterations of <italic>Fremyella diplosiphon</italic> strains in concentrations at 25.6 mg/L ampicillin <bold>(A,B)</bold>, 51.2 mg/L kanamycin <bold>(C,D)</bold> and 102.5 mg/L tetracycline <bold>(E,F)</bold> treatments. Representative sections of color bright field images were captured using a cytation 5 Cell Imaging Multi-Mode reader at 40&#x00D7; magnification bars, 100 &#x03BC;m.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmicb-13-930357-g006.tif"/>
</fig>
</sec>
</sec>
<sec id="S4" sec-type="discussion">
<title>Discussion</title>
<p>In the present study, we evaluated the effect of four different antibiotics on pigment autofluorescence and photosynthetic activity in two <italic>F. diplosiphon</italic> strains. Additionally, we observed membrane permeability and intracellular ROS production to determine the effect of antibiotic treatment on the strains.</p>
<sec id="S4.SS1">
<title>Alterations of Pigment Autofluorescence in Antibiotic-Treated <italic>Fremyella diplosiphon</italic></title>
<p>Of the four antibiotics tested in this study, ampicillin and cefotaxime belonged to the &#x03B2;-lactam group and are known to bind to the penicillin-binding protein of the prokaryotic cell (<xref ref-type="bibr" rid="B34">Stokes et al., 2019</xref>). The structural resemblance of the <italic>F. diplosiphon</italic> cell wall to gram-negative prokaryotes explains the sensitivity of cyanobacteria to &#x03B2;-lactam antibiotics (<xref ref-type="bibr" rid="B33">Springstein et al., 2020</xref>). Interestingly, phycocyanin and chlorophyll <italic>a</italic> autofluorescence in B481-SD was enhanced at lower ampicillin concentrations (0.2&#x2013;25.6 mg/L); however, its growth was significantly inhibited at concentrations above 51.2 mg/L. On the other hand, a substantial decline in pigment fluorescence was observed in B481-WT at concentrations higher than 3.2 mg/L ampicillin. Thus, significantly higher pigment fluorescence in B481-SD at these concentrations provide further evidence of the sterol dehydrogenase gene overexpression associated with ampicillin resistance. It is also known that the molecular configuration against &#x03B2;-lactam antibiotics is a mechanism for acquiring bacterial resistance (<xref ref-type="bibr" rid="B2">Alpay-Karaoglu et al., 2007</xref>; <xref ref-type="bibr" rid="B29">Sanganyado and Gwenzi, 2019</xref>). The significant reduction of pigment accumulation observed in cefotaxime at concentrations above 1.6 mg/L for B481-SD and 0.2 mg/L for B481-WT indicate the higher sensitivity of B481-WT to cefotaxime. Additionally, enhanced fluorescence of the strains exposed to kanamycin (0.2&#x2013;3.2 mg/L) and tetracycline (0.8&#x2013;12.8 mg/L) on day 6 indicate the hormetic effect of these antibiotics on stimulation and inhibition. Our results are in accordance with the findings of <xref ref-type="bibr" rid="B24">Liu et al. (2015)</xref>, who reported the toxic effect of amoxicillin at concentrations higher than 6.88 &#x03BC;g/L in <italic>Microcystis aeruginosa</italic>, while a growth-stimulating effect was observed at concentrations below. A similar biphasic effect was reported in <italic>Skeletonema costatum</italic> where exposure to florfenicol at &#x003C; 2.0 mg/L enhanced growth while inhibition was reported at &#x003E; 2.0 mg/L (<xref ref-type="bibr" rid="B22">Liu et al., 2012</xref>). As noted in our study, ampicillin, kanamycin, and tetracycline at higher concentrations inhibited <italic>F. diplosiphon</italic> pigment autofluorescence (<xref ref-type="fig" rid="F1">Figures 1</xref>, <xref ref-type="fig" rid="F2">2</xref>). Despite lowering the cefotaxime concentrations to 0.05 mg/L (<xref ref-type="fig" rid="F1">Figures 1</xref>, <xref ref-type="fig" rid="F2">2B,F</xref>), we did not observe the hormetic effect in B481-WT. Exposure to kanamycin and tetracycline resulted in approximately twice more remarkable pigment fluorescence in B481-SD than B481-WT, indicating higher tolerance of B481-SD to harmful antibiotics regardless of &#x03B2;-lactam resistance. In a previous study by <xref ref-type="bibr" rid="B13">Fathabad et al. (2019)</xref>, a 27.2% enhancement of total lipid content in B481-SD compared to B481-WT was reported, which was attributed to gene overexpression. The enhanced lipid production in B481-SD could be attributed to sustained membrane integrity, due to increased fatty acids that facilitates membrane repair in B48-SD (<xref ref-type="bibr" rid="B30">Sen, 2020</xref>). On the other hand, kanamycin and tetracycline inhibit protein synthesis by binding to the bacterial ribosomal subunit resulting in a misreading of the t-RNA. The inhibition of RNA translation could have resulted in protein-derived <italic>F. diplosiphon</italic> pigments as observed in our study. In a report by <xref ref-type="bibr" rid="B10">Daghrir and Drogui (2013)</xref>, tetracycline at 100 mg/L was reported to be detrimental to aquatic organisms. Although photocatalytic degradation of tetracycline occurs in a few days, the byproducts anhydrotetracycline and 4-epianhydrotetracycline have been reported to be more toxic than the primary compound (<xref ref-type="bibr" rid="B15">Halling-S&#x00F8;rensen et al., 2002</xref>). Thus, high concentrations of tetracycline ranging from 205 to 410mg/L were selected in this study. These residues might have also contributed to the pigment fluorescence of <italic>F. diplosiphon</italic>, as observed in our study.</p>
</sec>
<sec id="S4.SS2">
<title>Antibiotic Exposure Enhance <italic>Fremyella diplosiphon</italic> Membrane Permeability</title>
<p>Assessment of membrane integrity as a measure of extracellular LDH enzyme activity revealed a linear correlation (data not shown). In both strains treated with antibiotics, LDH activity correlated to phycocyanin and chlorophyll <italic>a</italic> accumulation in a dose-dependent manner, indicating a positive correlation between increased metabolic activity and membrane permeability prior to complete cell destruction. Antimicrobial agents such as ampicillin and cefotaxime that target prokaryotic cell walls are reported to be more effective in weakening membranes than ribosomal inhibitor antibiotics such as kanamycin and tetracycline (<xref ref-type="bibr" rid="B34">Stokes et al., 2019</xref>). These compounds are known to trigger intracellular signaling <italic>via</italic> the shifting of metabolic compounds such as glucose, glycerol, and pyruvate to lipid synthesis. In a study by <xref ref-type="bibr" rid="B23">Liu et al. (2011)</xref> weakening of the cell wall by ampicillin was reported to facilitate free fatty acids (FFA) secretion by reducing feedback inhibition of enzymes involved in the synthesis of fatty acid precursors, thus resulting in an overall increase in FFA production (<xref ref-type="bibr" rid="B2">Alpay-Karaoglu et al., 2007</xref>). Enhanced lipid production in <italic>Synechocystis</italic> species was correlated to a loss in membrane components as well (<xref ref-type="bibr" rid="B26">Oliveira et al., 2016</xref>). Thus, we hypothesize that membrane damage could lead to permeability changes as indicated by increased metabolic activity stimulating lipid synthesis and accumulation.</p>
<p>Production of ROS is pertinent when antibiotic concentrations above the threshold level can onset cellular stress (<xref ref-type="bibr" rid="B8">Chen et al., 2019</xref>). In cellular metabolism, a dynamic equilibrium between ROS generation and elimination is maintained due to the operation of antioxidant defense systems. In addition, a tremendous increase of ROS may cause oxidative damage resulting in cell injury and ultimately cell death due to protein and lipid damage and impairment of cyanobacterial homeostasis (<xref ref-type="bibr" rid="B12">Du et al., 2018</xref>). The reactive oxygen radicals generated have the potential to react with membrane lipids and protein (phycocyanin, chlorophyll a) structures in cyanobacteria. Our results revealed maximal ROS levels in both strains treated with ampicillin at 102.5 mg/L, with lower ROS levels in B481-SD compared to B481-WT. While B481-SD treated with cefotaxime at 0.2&#x2013;102.5 mg/L exhibited higher levels of ROS, it was not detected in B481-WT (<xref ref-type="supplementary-material" rid="FS1">Supplementary Figure 1D</xref>). It is possible that a reduction in the number of viable cells could have lowered ROS production in B481-WT. We hypothesize that the detrimental effect of cefotaxime could have resulted in higher ROS levels in the first few days of the experiment, while the unstable structure of oxygen radicals due to easy loss of unpaired electrons and elimination could be responsible for lower ROS at the end of the testing period. Both strains exposed to kanamycin at 102.5 mg/L revealed maximum ROS on day 6 and exhibited a similar growth paradigm at the concentrations tested. ROS production is generally caused by the leakage of electrons from the photosystem electron transport chain as part of the metabolism of photosynthetic organisms and plays a dynamic equilibrium in the operation of antioxidant defense system. A study on the analysis of the impact of superoxide dismutase (SOD) enzymes in 149 cyanobacterial strains has shown diverse SOD enzyme isoforms, indicating that the antioxidant mechanism that eliminates ROS could vary in different cyanobacterial strains (<xref ref-type="bibr" rid="B5">Boden et al., 2021</xref>).</p>
<p>Chlorophyll <italic>a</italic> is an important light-harvesting photosynthetic pigment in cyanobacteria, which plays a crucial role in energy absorption and transduction (<xref ref-type="bibr" rid="B21">Latifi et al., 2009</xref>). The electron transport capacity of photosynthetic pigments such as chlorophyll <italic>a</italic> is closely related to the quality of the photosynthetic apparatus and indicated by PSII activity (<italic>Fv/Fo</italic>). As the pigment content of cyanobacteria decrease, the thylakoid membrane becomes the active site due to cell wall damaging antibiotics such as penicillin and cephalosporins (<xref ref-type="bibr" rid="B24">Liu et al., 2015</xref>). The decrease in PSII activity of both strains at higher ampicillin, cefotaxime, and kanamycin concentrations of 51.2 and 102.5 mg/L on day 6 as observed in our study could be attributed to enhanced ROS production. Therefore, it is possible that reduced pigment functions could have occurred due to ROS-induced damage to the thylakoid membranes, particularly chlorophyll <italic>a</italic>.</p>
</sec>
</sec>
<sec id="S5" sec-type="conclusion">
<title>Conclusion</title>
<p>In this study, we investigated the effect of four antibiotics at varying concentrations on phycocyanin and chlorophyll <italic>a</italic> autofluorescence of <italic>F. diplosiphon</italic> strains. Significant increases in pigment accumulation at specific antibiotic concentrations pave the way for further studies to accomplish lipid synthesis for easy and efficient biofuel production. Future studies will aim toward enhancing membrane permeability in the B481-SD strain with antibiotics. In addition, the combined effect of antibiotics and zero-valent iron nanoparticles in enhancing specific lipid gene overexpression and transcript levels activity will be studied.</p>
</sec>
<sec id="S6" sec-type="data-availability">
<title>Data Availability Statement</title>
<p>The original contributions presented in this study are included in the article/<xref ref-type="supplementary-material" rid="FS1">Supplementary Material</xref>, further inquiries can be directed to the corresponding author.</p>
</sec>
<sec id="S7">
<title>Author Contributions</title>
<p>YY and BA designed and performed the experiments, analyzed, interpreted the data, and drafted the manuscript. MS gave critical comments on the article. VS designed, conceived the study, edited the manuscript, and obtained funding. All authors read and approved the final manuscript.</p>
</sec>
<sec id="conf1" sec-type="COI-statement">
<title>Conflict of Interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec id="pudiscl1" sec-type="disclaimer">
<title>Publisher&#x2019;s Note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
</body>
<back>
<sec id="S8" sec-type="funding-information">
<title>Funding</title>
<p>This research was funded by the National Science Foundation&#x2019;s Nanoscale Interactions Program (grant no. 1900966) and co-supported by Excellence in Research. Core support facilities partially provided by the National Institute of General Medical Sciences (grant no. 5UL1GM118973) and the National Institute on Minority Health and Health Disparities (grant no. 5U54MD013376) grants are acknowledged.</p>
</sec>
<sec id="S9" sec-type="supplementary-material">
<title>Supplementary Material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fmicb.2022.930357/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fmicb.2022.930357/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="Image_1.JPEG" id="FS1" mimetype="image/jpeg" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
<ref-list>
<title>References</title>
<ref id="B1"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Ajiboye</surname> <given-names>T. O.</given-names></name> <name><surname>Habibu</surname> <given-names>R. S.</given-names></name> <name><surname>Saidu</surname> <given-names>K.</given-names></name> <name><surname>Haliru</surname> <given-names>F. Z.</given-names></name> <name><surname>Ajiboye</surname> <given-names>H. O.</given-names></name> <name><surname>Aliyu</surname> <given-names>N. O.</given-names></name><etal/></person-group> (<year>2017</year>). <article-title>Involvement of oxidative stress in protocatechuic acid-mediated bacterial lethality.</article-title> <source><italic>Microbiologyopen</italic></source> <volume>6</volume>:<issue>e00472</issue>. <pub-id pub-id-type="doi">10.1002/mbo3.472</pub-id> <pub-id pub-id-type="pmid">28349673</pub-id></citation></ref>
<ref id="B2"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Alpay-Karaoglu</surname> <given-names>S.</given-names></name> <name><surname>Birol Ozgumus</surname> <given-names>O.</given-names></name> <name><surname>Sevim</surname> <given-names>E.</given-names></name> <name><surname>Kolayli</surname> <given-names>F.</given-names></name> <name><surname>Sevim</surname> <given-names>A.</given-names></name> <name><surname>Yesilgil</surname> <given-names>P.</given-names></name></person-group> (<year>2007</year>). <article-title>Investigation of antibiotic resistance profile and TEM-type &#x03B2;-lactamase gene carriage of ampicillin-resistant <italic>Escherichia coli</italic> strains isolated from drinking water.</article-title> <source><italic>Ann. Microbiol.</italic></source> <volume>57</volume>:<issue>281</issue>.</citation></ref>
<ref id="B3"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Bailey</surname> <given-names>C.</given-names></name> <name><surname>Spielmeyer</surname> <given-names>A.</given-names></name> <name><surname>Frings</surname> <given-names>R. M.</given-names></name> <name><surname>Hamscher</surname> <given-names>G.</given-names></name> <name><surname>Sch&#x00FC;ttrumpf</surname> <given-names>H.</given-names></name></person-group> (<year>2015</year>). <article-title>From agricultural fields to surface water systems: the overland transport of veterinary antibiotics.</article-title> <source><italic>J. Soils Sediments</italic></source> <volume>15</volume> <fpage>1630</fpage>&#x2013;<lpage>1634</lpage>. <pub-id pub-id-type="doi">10.1007/s11368-015-1140-4</pub-id></citation></ref>
<ref id="B4"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Baselga-Cervera</surname> <given-names>B.</given-names></name> <name><surname>Cordoba-Diaz</surname> <given-names>M.</given-names></name> <name><surname>Garc&#x00ED;a-Balboa</surname> <given-names>C.</given-names></name> <name><surname>Costas</surname> <given-names>E.</given-names></name> <name><surname>L&#x00F3;pez-Rodas</surname> <given-names>V.</given-names></name> <name><surname>Cordoba-Diaz</surname> <given-names>D.</given-names></name></person-group> (<year>2019</year>). <article-title>Assessing the effect of high doses of ampicillin on five marine and freshwater phytoplankton species: a biodegradation perspective.</article-title> <source><italic>J. Appl. Psychol.</italic></source> <volume>31</volume> <fpage>2999</fpage>&#x2013;<lpage>3010</lpage>. <pub-id pub-id-type="doi">10.1007/s10811-019-01823-8</pub-id></citation></ref>
<ref id="B5"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Boden</surname> <given-names>J. S.</given-names></name> <name><surname>Konhauser</surname> <given-names>K. O.</given-names></name> <name><surname>Robbins</surname> <given-names>L. J.</given-names></name> <name><surname>S&#x00E1;nchez-Baracaldo</surname> <given-names>P.</given-names></name></person-group> (<year>2021</year>). <article-title>Timing the evolution of antioxidant enzymes in cyanobacteria.</article-title> <source><italic>Nat. Commun.</italic></source> <volume>12</volume>:<issue>4742</issue>. <pub-id pub-id-type="doi">10.1038/s41467-021-24396-y</pub-id> <pub-id pub-id-type="pmid">34362891</pub-id></citation></ref>
<ref id="B6"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Browne</surname> <given-names>A. J.</given-names></name> <name><surname>Chipeta</surname> <given-names>M. G.</given-names></name> <name><surname>Haines-Woodhouse</surname> <given-names>G.</given-names></name> <name><surname>Kumaran</surname> <given-names>E. P. A.</given-names></name> <name><surname>Hamadani</surname> <given-names>B. H. K.</given-names></name> <name><surname>Zaraa</surname> <given-names>S.</given-names></name><etal/></person-group> (<year>2021</year>). <article-title>Global antibiotic consumption and usage in humans, 2000&#x2013;18: a spatial modelling study.</article-title> <source><italic>Lancet Planet. Health</italic></source> <volume>5</volume> <fpage>e893</fpage>&#x2013;<lpage>e904</lpage>. <pub-id pub-id-type="doi">10.1016/S2542-5196(21)00280-1</pub-id></citation></ref>
<ref id="B7"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Busch</surname> <given-names>A. W. U.</given-names></name> <name><surname>Montgomery</surname> <given-names>B. L.</given-names></name></person-group> (<year>2015</year>). <article-title>The tryptophan-rich sensory protein (TSPO) is involved in stress-related and light-dependent processes in the cyanobacterium fremyella diplosiphon.</article-title> <source><italic>Front. Microbiol.</italic></source> <volume>6</volume>:<issue>1393</issue>. <pub-id pub-id-type="doi">10.3389/fmicb.2015.01393</pub-id> <pub-id pub-id-type="pmid">26696996</pub-id></citation></ref>
<ref id="B8"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Chen</surname> <given-names>X.</given-names></name> <name><surname>Yin</surname> <given-names>H.</given-names></name> <name><surname>Li</surname> <given-names>G.</given-names></name> <name><surname>Wang</surname> <given-names>W.</given-names></name> <name><surname>Wong</surname> <given-names>P. K.</given-names></name> <name><surname>Zhao</surname> <given-names>H.</given-names></name><etal/></person-group> (<year>2019</year>). <article-title>Antibiotic-resistance gene transfer in antibiotic-resistance bacteria under different light irradiation: implications from oxidative stress and gene expression.</article-title> <source><italic>Water Res.</italic></source> <volume>149</volume> <fpage>282</fpage>&#x2013;<lpage>291</lpage>. <pub-id pub-id-type="doi">10.1016/j.watres.2018.11.019</pub-id> <pub-id pub-id-type="pmid">30465986</pub-id></citation></ref>
<ref id="B9"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Cui</surname> <given-names>M.</given-names></name> <name><surname>Liu</surname> <given-names>Y.</given-names></name> <name><surname>Zhang</surname> <given-names>J.</given-names></name></person-group> (<year>2020</year>). <article-title>Sulfamethoxazole and tetracycline induced alterations in biomass, photosynthesis, lipid productivity, and proteomic expression of Synechocystis sp. PCC 6803.</article-title> <source><italic>Environ. Sci. Pollut. Res.</italic></source> <volume>27</volume> <fpage>30437</fpage>&#x2013;<lpage>30447</lpage>. <pub-id pub-id-type="doi">10.1007/s11356-020-09327-6</pub-id> <pub-id pub-id-type="pmid">32462618</pub-id></citation></ref>
<ref id="B10"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Daghrir</surname> <given-names>R.</given-names></name> <name><surname>Drogui</surname> <given-names>P.</given-names></name></person-group> (<year>2013</year>). <article-title>Tetracycline antibiotics in the environment: a review.</article-title> <source><italic>Environ. Chem. Lett.</italic></source> <volume>11</volume> <fpage>209</fpage>&#x2013;<lpage>227</lpage>. <pub-id pub-id-type="doi">10.1007/s10311-013-0404-8</pub-id></citation></ref>
<ref id="B11"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Dias</surname> <given-names>E.</given-names></name> <name><surname>Oliveira</surname> <given-names>M.</given-names></name> <name><surname>Jones-Dias</surname> <given-names>D.</given-names></name> <name><surname>Vasconcelos</surname> <given-names>V.</given-names></name> <name><surname>Ferreira</surname> <given-names>E.</given-names></name> <name><surname>Manageiro</surname> <given-names>V.</given-names></name><etal/></person-group> (<year>2015</year>). <article-title>Assessing the antibiotic susceptibility of freshwater cyanobacteria spp.</article-title> <source><italic>Front. Microbiol.</italic></source> <volume>6</volume>:<issue>799</issue>. <pub-id pub-id-type="doi">10.3389/fmicb.2015.00799</pub-id> <pub-id pub-id-type="pmid">26322027</pub-id></citation></ref>
<ref id="B12"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Du</surname> <given-names>Y.</given-names></name> <name><surname>Wang</surname> <given-names>J.</given-names></name> <name><surname>Zhu</surname> <given-names>F.</given-names></name> <name><surname>Mai</surname> <given-names>D.</given-names></name> <name><surname>Xiang</surname> <given-names>Z.</given-names></name> <name><surname>Chen</surname> <given-names>J.</given-names></name><etal/></person-group> (<year>2018</year>). <article-title>Comprehensive assessment of three typical antibiotics on cyanobacteria (Microcystis aeruginosa): the impact and recovery capability.</article-title> <source><italic>Ecotoxicol. Environ. Saf.</italic></source> <volume>160</volume> <fpage>84</fpage>&#x2013;<lpage>93</lpage>. <pub-id pub-id-type="doi">10.1016/j.ecoenv.2018.05.035</pub-id> <pub-id pub-id-type="pmid">29793205</pub-id></citation></ref>
<ref id="B13"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Fathabad</surname> <given-names>G. S.</given-names></name> <name><surname>Arumanayagam</surname> <given-names>A. C. S.</given-names></name> <name><surname>Tabatabai</surname> <given-names>B.</given-names></name> <name><surname>Chen</surname> <given-names>H.</given-names></name> <name><surname>Lu</surname> <given-names>J.</given-names></name> <name><surname>Sitther</surname> <given-names>V.</given-names></name></person-group> (<year>2019</year>). <article-title>Augmenting Fremyella diplosiphon cellular lipid content and unsaturated fatty acid methyl esters via sterol desaturase gene overexpression.</article-title> <source><italic>Appl. Biochem. Biotechnol.</italic></source> <volume>189</volume> <fpage>1127</fpage>&#x2013;<lpage>1140</lpage>. <pub-id pub-id-type="doi">10.1007/s12010-019-03055-5</pub-id> <pub-id pub-id-type="pmid">31168708</pub-id></citation></ref>
<ref id="B14"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Gonz&#x00E1;lez-Pleiter</surname> <given-names>M.</given-names></name> <name><surname>Gonzalo</surname> <given-names>S.</given-names></name> <name><surname>Rodea-Palomares</surname> <given-names>I.</given-names></name> <name><surname>Legan&#x00E9;s</surname> <given-names>F.</given-names></name> <name><surname>Rosal</surname> <given-names>R.</given-names></name> <name><surname>Boltes</surname> <given-names>K.</given-names></name><etal/></person-group> (<year>2013</year>). <article-title>Toxicity of five antibiotics and their mixtures towards photosynthetic aquatic organisms: implications for environmental risk assessment.</article-title> <source><italic>Water Res.</italic></source> <volume>47</volume> <fpage>2050</fpage>&#x2013;<lpage>2064</lpage>. <pub-id pub-id-type="doi">10.1016/j.watres.2013.01.020</pub-id> <pub-id pub-id-type="pmid">23399078</pub-id></citation></ref>
<ref id="B15"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Halling-S&#x00F8;rensen</surname> <given-names>B.</given-names></name> <name><surname>Sengel&#x00F8;v</surname> <given-names>G.</given-names></name> <name><surname>Tj&#x00F8;rnelund</surname> <given-names>J.</given-names></name></person-group> (<year>2002</year>). <article-title>Toxicity of tetracyclines and tetracycline degradation products to environmentally relevant bacteria, including selected tetracycline-resistant bacteria.</article-title> <source><italic>Arch. Environ. Contam. Toxicol.</italic></source> <volume>42</volume> <fpage>263</fpage>&#x2013;<lpage>271</lpage>. <pub-id pub-id-type="doi">10.1007/s00244-001-0017-2</pub-id> <pub-id pub-id-type="pmid">11910453</pub-id></citation></ref>
<ref id="B16"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Kapoor</surname> <given-names>G.</given-names></name> <name><surname>Saigal</surname> <given-names>S.</given-names></name> <name><surname>Elongavan</surname> <given-names>A.</given-names></name></person-group> (<year>2017</year>). <article-title>Action and resistance mechanisms of antibiotics: a guide for clinicians.</article-title> <source><italic>J. Anaesthesiol. Clin. Pharmacol.</italic></source> <volume>33</volume> <fpage>300</fpage>&#x2013;<lpage>305</lpage>. <pub-id pub-id-type="doi">10.4103/joacp.JOACP_349_15</pub-id></citation></ref>
<ref id="B17"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Kim</surname> <given-names>C.</given-names></name> <name><surname>Ryu</surname> <given-names>H. D.</given-names></name> <name><surname>Chung</surname> <given-names>E. G.</given-names></name> <name><surname>Kim</surname> <given-names>Y.</given-names></name></person-group> (<year>2018</year>). <article-title>Determination of 18 veterinary antibiotics in environmental water using high-performance liquid chromatography-q-orbitrap combined with on-line solid-phase extraction.</article-title> <source><italic>J. Chromatogr. B.</italic></source> <volume>1084</volume> <fpage>158</fpage>&#x2013;<lpage>165</lpage>. <pub-id pub-id-type="doi">10.1016/j.jchromb.2018.03.038</pub-id> <pub-id pub-id-type="pmid">29604614</pub-id></citation></ref>
<ref id="B18"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Kouda</surname> <given-names>K.</given-names></name> <name><surname>Iki</surname> <given-names>M.</given-names></name></person-group> (<year>2010</year>). <article-title>Beneficial effects of mild stress (Hormetic Effects): dietary restriction and health.</article-title> <source><italic>J. Physiol. Anthropol.</italic></source> <volume>29</volume> <fpage>127</fpage>&#x2013;<lpage>132</lpage>. <pub-id pub-id-type="doi">10.2114/jpa2.29.127</pub-id> <pub-id pub-id-type="pmid">20686325</pub-id></citation></ref>
<ref id="B19"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Kulkarni</surname> <given-names>P.</given-names></name> <name><surname>Olson</surname> <given-names>N. D.</given-names></name> <name><surname>Raspanti</surname> <given-names>G. A.</given-names></name> <name><surname>Goldstein</surname> <given-names>R. E. R.</given-names></name> <name><surname>Gibbs</surname> <given-names>S. G.</given-names></name> <name><surname>Sapkota</surname> <given-names>A.</given-names></name><etal/></person-group> (<year>2017</year>). <article-title>Antibiotic concentrations decrease during wastewater treatment but persist at low levels in reclaimed water.</article-title> <source><italic>Int. J. Environ. Res. Public Health</italic></source> <volume>14</volume>:<issue>668</issue>. <pub-id pub-id-type="doi">10.3390/ijerph14060668</pub-id> <pub-id pub-id-type="pmid">28635638</pub-id></citation></ref>
<ref id="B20"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>K&#x00FC;mmerer</surname> <given-names>K.</given-names></name></person-group> (<year>2009</year>). <article-title>Antibiotics in the aquatic environment - A review - Part I.</article-title> <source><italic>Chemosphere</italic></source> <volume>75</volume> <fpage>417</fpage>&#x2013;<lpage>434</lpage>. <pub-id pub-id-type="doi">10.1016/j.chemosphere.2008.11.086</pub-id> <pub-id pub-id-type="pmid">19185900</pub-id></citation></ref>
<ref id="B21"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Latifi</surname> <given-names>A.</given-names></name> <name><surname>Ruiz</surname> <given-names>M.</given-names></name> <name><surname>Zhang</surname> <given-names>C. C.</given-names></name></person-group> (<year>2009</year>). <article-title>Oxidative stress in cyanobacteria.</article-title> <source><italic>FEMS Microbiol. Rev.</italic></source> <volume>33</volume> <fpage>258</fpage>&#x2013;<lpage>278</lpage>. <pub-id pub-id-type="doi">10.1111/j.1574-6976.2008.00134.x</pub-id> <pub-id pub-id-type="pmid">18834454</pub-id></citation></ref>
<ref id="B22"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Liu</surname> <given-names>W.</given-names></name> <name><surname>Ming</surname> <given-names>Y.</given-names></name> <name><surname>Huang</surname> <given-names>Z.</given-names></name> <name><surname>Li</surname> <given-names>P.</given-names></name></person-group> (<year>2012</year>). <article-title>Impacts of florfenicol on marine diatom Skeletonema costatum through photosynthesis inhibition and oxidative damages.</article-title> <source><italic>Plant Physiol. Biochem.</italic></source> <volume>60</volume> <fpage>165</fpage>&#x2013;<lpage>170</lpage>. <pub-id pub-id-type="doi">10.1016/j.plaphy.2012.08.009</pub-id> <pub-id pub-id-type="pmid">22960224</pub-id></citation></ref>
<ref id="B23"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Liu</surname> <given-names>X.</given-names></name> <name><surname>Sheng</surname> <given-names>J.</given-names></name> <name><surname>Curtiss Iii</surname> <given-names>R.</given-names></name></person-group> (<year>2011</year>). <article-title>Fatty acid production in genetically modified cyanobacteria.</article-title> <source><italic>Proc. Natl. Acad. Sci. U. S. A.</italic></source> <volume>108</volume> <fpage>6899</fpage>&#x2013;<lpage>6904</lpage>. <pub-id pub-id-type="doi">10.1073/pnas.1103014108/-/DCSupplemental</pub-id> <pub-id pub-id-type="pmid">21482809</pub-id></citation></ref>
<ref id="B24"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Liu</surname> <given-names>Y.</given-names></name> <name><surname>Chen</surname> <given-names>X.</given-names></name> <name><surname>Zhang</surname> <given-names>J.</given-names></name> <name><surname>Gao</surname> <given-names>B.</given-names></name></person-group> (<year>2015</year>). <article-title>Hormesis effects of amoxicillin on growth and cellular biosynthesis of Microcystis aeruginosa at different nitrogen levels.</article-title> <source><italic>Microb. Ecol.</italic></source> <volume>69</volume> <fpage>608</fpage>&#x2013;<lpage>617</lpage>. <pub-id pub-id-type="doi">10.1007/s00248-014-0528-9</pub-id> <pub-id pub-id-type="pmid">25388759</pub-id></citation></ref>
<ref id="B25"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Norvill</surname> <given-names>Z. N.</given-names></name> <name><surname>Shilton</surname> <given-names>A.</given-names></name> <name><surname>Guieysse</surname> <given-names>B.</given-names></name></person-group> (<year>2016</year>). <article-title>Emerging contaminant degradation and removal in algal wastewater treatment ponds: identifying the research gaps.</article-title> <source><italic>J. Hazard. Mater.</italic></source> <volume>313</volume> <fpage>291</fpage>&#x2013;<lpage>309</lpage>. <pub-id pub-id-type="doi">10.1016/j.jhazmat.2016.03.085</pub-id> <pub-id pub-id-type="pmid">27135171</pub-id></citation></ref>
<ref id="B26"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Oliveira</surname> <given-names>P.</given-names></name> <name><surname>Martins</surname> <given-names>N. M.</given-names></name> <name><surname>Santos</surname> <given-names>M.</given-names></name> <name><surname>Pinto</surname> <given-names>F.</given-names></name> <name><surname>B&#x00FC;ttel</surname> <given-names>Z.</given-names></name> <name><surname>Couto</surname> <given-names>N. A. S.</given-names></name><etal/></person-group> (<year>2016</year>). <article-title>The versatile TolC-like Slr1270 in the cyanobacterium Synechocystis.</article-title> <source><italic>Environ. Microbiol.</italic></source> <volume>18</volume> <fpage>486</fpage>&#x2013;<lpage>502</lpage>. <pub-id pub-id-type="doi">10.1111/1462-2920.13172</pub-id> <pub-id pub-id-type="pmid">26663346</pub-id></citation></ref>
<ref id="B27"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Pan</surname> <given-names>M.</given-names></name> <name><surname>Lyu</surname> <given-names>T.</given-names></name> <name><surname>Zhan</surname> <given-names>L.</given-names></name> <name><surname>Matamoros</surname> <given-names>V.</given-names></name> <name><surname>Angelidaki</surname> <given-names>I.</given-names></name> <name><surname>Cooper</surname> <given-names>M.</given-names></name><etal/></person-group> (<year>2021</year>). <article-title>Mitigating antibiotic pollution using cyanobacteria: removal efficiency, pathways and metabolism.</article-title> <source><italic>Water Res.</italic></source> <volume>190</volume>:<issue>116735</issue>. <pub-id pub-id-type="doi">10.1016/j.watres.2020.116735</pub-id> <pub-id pub-id-type="pmid">33352526</pub-id></citation></ref>
<ref id="B28"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Roha&#x00EC;&#x010D;ek</surname> <given-names>K.</given-names></name> <name><surname>Barta&#x00EC;k</surname> <given-names>M.</given-names></name></person-group> (<year>1999</year>). <article-title>Technique of the modulated chlorophyll fluorescence: basic concepts, useful parameters, and Some applications.</article-title> <source><italic>Photosynthetica</italic></source> <volume>37</volume>:<issue>339</issue>.</citation></ref>
<ref id="B29"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Sanganyado</surname> <given-names>E.</given-names></name> <name><surname>Gwenzi</surname> <given-names>W.</given-names></name></person-group> (<year>2019</year>). <article-title>Antibiotic resistance in drinking water systems: occurrence, removal, and human health risks.</article-title> <source><italic>Sci. Total Environ.</italic></source> <volume>669</volume> <fpage>785</fpage>&#x2013;<lpage>797</lpage>. <pub-id pub-id-type="doi">10.1016/j.scitotenv.2019.03.162</pub-id> <pub-id pub-id-type="pmid">30897437</pub-id></citation></ref>
<ref id="B30"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Sen</surname> <given-names>S.</given-names></name></person-group> (<year>2020</year>). <article-title>Cyanobacterial membrane biology under environmental stresses with particular reference to photosynthesis and photomorphogenesis</article-title>, in <source><italic>Advances in Cyanobacterial Biology.</italic></source> (<publisher-loc>Amsterdam</publisher-loc>: <publisher-name>Elsevier</publisher-name>), <fpage>73</fpage>&#x2013;<lpage>84</lpage>. <pub-id pub-id-type="doi">10.1016/b978-0-12-819311-2.00006-1</pub-id></citation></ref>
<ref id="B31"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Shang</surname> <given-names>A. H.</given-names></name> <name><surname>Ye</surname> <given-names>J.</given-names></name> <name><surname>Chen</surname> <given-names>D. H.</given-names></name> <name><surname>Lu</surname> <given-names>X. X.</given-names></name> <name><surname>Lu</surname> <given-names>H. D.</given-names></name> <name><surname>Liu</surname> <given-names>C. N.</given-names></name><etal/></person-group> (<year>2015</year>). <article-title>Physiological effects of tetracycline antibiotic pollutants on non-target aquatic Microcystis aeruginosa.</article-title> <source><italic>J. Environ. Sci. Health B Pestic.</italic></source> <volume>50</volume> <fpage>809</fpage>&#x2013;<lpage>818</lpage>. <pub-id pub-id-type="doi">10.1080/03601234.2015.1058100</pub-id> <pub-id pub-id-type="pmid">26357891</pub-id></citation></ref>
<ref id="B32"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Snow</surname> <given-names>D. D.</given-names></name> <name><surname>Bartelt-Hunt</surname> <given-names>S. L.</given-names></name> <name><surname>Devivo</surname> <given-names>S.</given-names></name> <name><surname>Saunders</surname> <given-names>S.</given-names></name> <name><surname>Cassada</surname> <given-names>D. A.</given-names></name></person-group> (<year>2009</year>). <article-title>Detection, occurrence, and fate of emerging contaminants in agricultural environments.</article-title> <source><italic>Water Environ. Res.</italic></source> <volume>81</volume> <fpage>941</fpage>&#x2013;<lpage>958</lpage>. <pub-id pub-id-type="doi">10.2175/106143009x461573</pub-id></citation></ref>
<ref id="B33"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Springstein</surname> <given-names>B. L.</given-names></name> <name><surname>N&#x00FC;rnberg</surname> <given-names>D. J.</given-names></name> <name><surname>Weiss</surname> <given-names>G. L.</given-names></name> <name><surname>Pilhofer</surname> <given-names>M.</given-names></name> <name><surname>Stucken</surname> <given-names>K.</given-names></name></person-group> (<year>2020</year>). <article-title>Structural determinants and their role in cyanobacterial morphogenesis.</article-title> <source><italic>Life</italic></source> <volume>10</volume> <fpage>1</fpage>&#x2013;<lpage>33</lpage>. <pub-id pub-id-type="doi">10.3390/life10120355</pub-id> <pub-id pub-id-type="pmid">33348886</pub-id></citation></ref>
<ref id="B34"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Stokes</surname> <given-names>J. M.</given-names></name> <name><surname>Lopatkin</surname> <given-names>A. J.</given-names></name> <name><surname>Lobritz</surname> <given-names>M. A.</given-names></name> <name><surname>Collins</surname> <given-names>J. J.</given-names></name></person-group> (<year>2019</year>). <article-title>Bacterial Metabolism and Antibiotic Efficacy.</article-title> <source><italic>Cell Metabol.</italic></source> <volume>30</volume> <fpage>251</fpage>&#x2013;<lpage>259</lpage>. <pub-id pub-id-type="doi">10.1016/j.cmet.2019.06.009</pub-id> <pub-id pub-id-type="pmid">31279676</pub-id></citation></ref>
<ref id="B35"><citation citation-type="journal"><collab>U.S. Food and Drug Administration</collab> (<year>2019</year>). <source><italic>Summary Report on Antimicrobials Sold or Distributed for Use in Food-Producing Animals.</italic></source> <publisher-loc>Silver Spring, MD</publisher-loc>: <publisher-name>U.S. Food and Drug Administration</publisher-name>.</citation></ref>
<ref id="B36"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Wan</surname> <given-names>J.</given-names></name> <name><surname>Guo</surname> <given-names>P.</given-names></name> <name><surname>Peng</surname> <given-names>X.</given-names></name> <name><surname>Wen</surname> <given-names>K.</given-names></name></person-group> (<year>2015</year>). <article-title>Effect of erythromycin exposure on the growth, antioxidant system and photosynthesis of Microcystis flos-aquae.</article-title> <source><italic>J. Hazard. Mater</italic></source> <volume>283</volume> <fpage>778</fpage>&#x2013;<lpage>786</lpage>. <pub-id pub-id-type="doi">10.1016/j.jhazmat.2014.10.026</pub-id> <pub-id pub-id-type="pmid">25464321</pub-id></citation></ref>
<ref id="B37"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Wejnerowski</surname> <given-names>&#x0141;</given-names></name> <name><surname>Rzymski</surname> <given-names>P.</given-names></name> <name><surname>Kokoci&#x0144;ski</surname> <given-names>M.</given-names></name> <name><surname>Meriluoto</surname> <given-names>J.</given-names></name></person-group> (<year>2018</year>). <article-title>The structure and toxicity of winter cyanobacterial bloom in a eutrophic lake of the temperate zone.</article-title> <source><italic>Ecotoxicology</italic></source> <volume>27</volume> <fpage>752</fpage>&#x2013;<lpage>760</lpage>. <pub-id pub-id-type="doi">10.1007/s10646-018-1957-x</pub-id> <pub-id pub-id-type="pmid">29934736</pub-id></citation></ref>
<ref id="B38"><citation citation-type="journal"><collab>WHO</collab> (<year>2016</year>). <source><italic>Report on Surveillance of Antibiotic Consumption.</italic></source> <publisher-loc>Geneva</publisher-loc>: <publisher-name>WHO</publisher-name>.</citation></ref>
<ref id="B39"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Wu</surname> <given-names>Y.</given-names></name> <name><surname>Wan</surname> <given-names>L.</given-names></name> <name><surname>Zhang</surname> <given-names>W.</given-names></name> <name><surname>Ding</surname> <given-names>H.</given-names></name> <name><surname>Yang</surname> <given-names>W.</given-names></name></person-group> (<year>2020</year>). <article-title>Resistance of cyanobacteria Microcystis aeruginosa to erythromycin with multiple exposure.</article-title> <source><italic>Chemosphere</italic></source> <volume>249</volume>:<issue>126147</issue>. <pub-id pub-id-type="doi">10.1016/j.chemosphere.2020.126147</pub-id> <pub-id pub-id-type="pmid">32062559</pub-id></citation></ref>
</ref-list>
</back>
</article>