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<article article-type="review-article" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:mml="http://www.w3.org/1998/Math/MathML" xml:lang="en">
<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">JRENHEP</journal-id>
<journal-title-group>
<journal-title>Journal of Renal and Hepatic Disorders</journal-title>
<abbrev-journal-title>JRENHEP</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">2207-3744</issn>
<publisher>
<publisher-name>Codon Publications</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="publisher-id">JRENHEP-4-001</article-id>
<article-id pub-id-type="doi">10.15586/jrenhep.2020.66</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>REVIEW ARTICLE</subject>
</subj-group>
</article-categories>
<title-group>
<article-title>Manganese-Induced Nephrotoxicity Is Mediated through Oxidative Stress and Mitochondrial Impairment</article-title>
</title-group>
<contrib-group content-type="authors">
<contrib contrib-type="author"><name><surname>Niknahad</surname> <given-names>Amir Mohammad</given-names></name><xref ref-type="aff" rid="aff1">1</xref><xref ref-type="aff" rid="aff2">2</xref></contrib> 
<contrib contrib-type="author"><name><surname>Ommati</surname> <given-names>Mohammad Mehdi</given-names></name><xref ref-type="aff" rid="aff3">3</xref></contrib> 
<contrib contrib-type="author"><name><surname>Farshad</surname> <given-names>Omid</given-names></name><xref ref-type="aff" rid="aff1">1</xref></contrib> 
<contrib contrib-type="author" corresp="yes"><name><surname>Moezi</surname> <given-names>Leila</given-names></name><xref ref-type="aff" rid="aff1">1</xref><xref ref-type="aff" rid="aff2">2</xref><xref ref-type="corresp" rid="cor1"/></contrib> 
<contrib contrib-type="author" corresp="yes"><contrib-id contrib-id-type="orcid">https://orcid.org/0000-0002-7038-9838</contrib-id> <name><surname>Heidari</surname> <given-names>Reza</given-names></name><xref ref-type="aff" rid="aff1">1</xref><xref ref-type="corresp" rid="cor1"/></contrib>
<aff id="aff1"><label>1</label>Pharmaceutical Sciences Research Center, Shiraz University of Medical Sciences, Shiraz, Iran;</aff> 
<aff id="aff2"><label>2</label>Department of Pharmacology, School of Medicine, Shiraz University of Medical Sciences, Shiraz, Iran;</aff> 
<aff id="aff3"><label>3</label>College of Life Sciences, Shanxi Agricultural University, Taigu, Shanxi, Peoples&#x2019; Republic of China</aff>
</contrib-group>
<author-notes>
<corresp id="cor1"><italic>Author for correspondence</italic>: Reza Heidari and Leila Moezi, Pharmaceutical Sciences Research Center, Shiraz University of Medical Sciences, Shiraz, Iran. Fax: 07131242626, Tel: 07131242627-282. Emails: <email>rezaheidari@hotmail.com</email>; <email>reidari@sums.ac.ir</email>; <email>moezil@sums.ac.ir</email>. ORCID: <ext-link ext-link-type="uri" xlink:href="https://orcid.org/0000-0002-7038-9838">https://orcid.org/0000-0002-7038-9838</ext-link>.</corresp>
</author-notes>
<pub-date pub-type="epub">
<day>09</day>
<month>06</month>
<year>2020</year>
</pub-date>
<pub-date pub-type="collection"><month>06</month><year>2020</year></pub-date>
<volume>4</volume>
<issue>2</issue>
<fpage>1</fpage>
<lpage>10</lpage>
<history>
<date date-type="received"><day>23</day><month>04</month><year>2020</year></date>
<date date-type="accepted"><day>13</day><month>05</month><year>2020</year></date>
</history>
<permissions>
<copyright-statement><italic>Copyright</italic>: Niknahad AM, et al.</copyright-statement>
<copyright-year>2020</copyright-year>
<license license-type="open-access" xlink:href="http://creativecommons.org/licenses/by/4.0/">
<license-p>This open access article is licensed under Creative Commons Attribution 4.0 International (CC BY 4.0). <ext-link ext-link-type="uri" xlink:href="http://creativecommons.org/">http://creativecommons.org/</ext-link></license-p>
</license>
</permissions>
<abstract>
<p>Manganese (Mn) is an essential element that is incorporated in various metabolic pathways and enzyme structures. On the other hand, a range of adverse effects has been described in association with Mn overexposure. Mn is a well-known neurotoxic agent in mammals. Renal injury is another adverse effect associated with Mn intoxication. No precise mechanism for Mn nephrotoxicity has been identified so far. The current study was designed to evaluate the potential mechanisms of Mn-induced renal injury. Rats were treated with Mn (20 and 40 mg/mL, respectively, in drinking water) for 30 consecutive days. Markers of oxidative stress, as well as several mitochondrial indices, were assessed in the kidney tissue. Renal injury was evident in Mn-treated animals, as judged by a significant increase in serum BUN and creatinine. Moreover, urinalysis revealed a significant increase in urine glucose, phosphate, and protein in Mn-treated rats. Kidney histopathological alterations, including tubular atrophy, interstitial inflammation, and necrosis, were also detected in Mn-treated animals. Biomarkers of oxidative stress, including an increment in reactive oxygen species (ROS), lipid peroxidation, and oxidized glutathione (GSSG), were detected in Mn-treated groups. On the other hand, kidney glutathione (GSH) stores and total antioxidant capacity were depleted in Mn groups. Mn exposure was associated with significant mitochondrial depolarization, decreased mitochondrial dehydrogenases activity, mitochondrial permeabilization, and depletion of adenosine tri-phosphate (ATP) content. These data highlight oxidative stress and mitochondrial impairment as potential mechanisms involved in Mn-induced renal injury.</p>
</abstract>
<kwd-group>
<kwd>energy crisis</kwd>
<kwd>manganism</kwd>
<kwd>mitochondria</kwd>
<kwd>renal failure</kwd>
<kwd>serum electrolyte waste</kwd>
</kwd-group>
</article-meta>
</front>
<body>
<sec id="S1" sec-type="intro">
<title>Introduction</title>
<p>Manganese (Mn) is a trace element incorporated in several metabolic pathways and in the structures of some vital enzymes (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref2">2</xref>). However, it has also been found that Mn overexposure is associated with several deleterious adverse effects, such as neurotoxicity (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref3">3</xref>&#x2013;<xref ref-type="bibr" rid="ref5">5</xref>). Renal injury and disturbances of serum electrolytes are the other adverse effects associated with Mn overexposure (<xref ref-type="bibr" rid="ref6">6</xref>&#x2013;<xref ref-type="bibr" rid="ref8">8</xref>). There is no precise mechanism for Mn-induced nephrotoxicity.</p>
<p>The mechanism of Mn neurotoxicity is widely investigated (<xref ref-type="bibr" rid="ref9">9</xref>). It has been found that Mn-induced oxidative stress plays a central role in the adverse effects of this metal on the nervous system (<xref ref-type="bibr" rid="ref9">9</xref>&#x2013;<xref ref-type="bibr" rid="ref12">12</xref>). It has been reported that Mn accumulates in cellular mitochondria through calcium (Ca<sup>2+</sup>) channels (<xref ref-type="bibr" rid="ref2">2</xref>). Hence, cellular mitochondria are critical targets for Mn cytotoxicity. Mitochondrial depolarization, mitochondria swelling, increased mitochondria-mediated reactive oxygen species (ROS) formation, and mitochondria-mediated cell death have been reported in different experimental models that investigated Mn neurotoxicity (<xref ref-type="bibr" rid="ref9">9</xref>&#x2013;<xref ref-type="bibr" rid="ref13">13</xref>).</p>
<p>Renal tissue contains numerous mitochondria, the proper functioning of which guarantee appropriate energy (ATP) level required for the reabsorption process of chemicals (<xref ref-type="bibr" rid="ref14">14</xref>&#x2013;<xref ref-type="bibr" rid="ref16">16</xref>). The mechanism of nephrotoxicity induced by several xenobiotics relies on mitochondrial impairment and mitochondria-mediated cell death (<xref ref-type="bibr" rid="ref17">17</xref>). Oxidative stress and mitochondrial injury are two mechanistically related events (<xref ref-type="bibr" rid="ref18">18</xref>). Hence, mitochondrial impairment could deteriorate oxidative stress and vice versa.</p>
<p>As already mentioned, there is no precise mechanism for Mn-induced renal injury. The current study was designed to evaluate the role of oxidative stress and mitochondrial impairment in the pathogenesis of Mn nephrotoxicity. Rats were exposed to Mn for 30 consecutive days. Several biomarkers in serum and urine, as well as histopathological alterations and oxidative stress markers in renal tissue, were evaluated. Moreover, kidney tissue mitochondria were isolated and assessed.</p></sec>
<sec id="S2" sec-type="materials|methods">
<title>Materials and Methods</title>
<sec id="S2_1">
<title>Reagents</title>
<p>3-[4,5dimethylthiazol-2-yl]-2,5-diphenyltetrazolium bromide (MTT), iodoacetic acid, potassium hydroxide, bovine serum albumin (BSA), methanol high performance liquid chromatography (HPLC) grade, 3-(N-morpholino) propane sulfonic acid (MOPS), 4,2Hydroxyethyl,1-piperazineethanesulfonic acid (HEPES), dimethyl sulfoxide (DMSO), thiobarbituric acid (TBA), glacial acetic acid, glutathione (GSH), malondialdehyde (MDA), 2&#x2032;,7&#x2032; Dichlorofluorescein diacetate (DCFH-DA), acetonitrile HPLC grade, ethylene glycol-bis (2-aminoethyl ether)-N, N, N&#x2032;, N&#x2032;-tetraacetic acid (EGTA), sucrose, dithiothreitol (DTT), sodium chloride, and Rhodamine 123 were obtained from Sigma Chemical Co. (St. Louis, MO, USA). Manganese chloride (MnCl<sub>2</sub>), trichloroacetic acid (TCA), and hydroxymethyl aminomethane hydrochloride (Tris-HCl) were purchased from Merck (Darmstadt, Germany).</p></sec>
<sec id="S2_2">
<title>Animals and treatments</title>
<p>Mature male Sprague&#x2013;Dawley rats (200&#x2013;250 g, live weight; n = 24) were obtained from Shiraz University of Medicine, Shiraz, Iran. Rats were maintained under standard conditions (22&#x2013;24&#x00B0;C; 12:12 h, photo schedule; appropriate ventilation; and 40 &#x00B1; 2% relative humidity). Animals had free access to tap water and a commercial rodents chow diet (RoyanFeed<sup>&#x00AE;</sup>, Isfahan, Iran). All procedures on experimental animals were performed in compliance with the ethical guidelines approved by the Shiraz University of Medical Sciences ethics committee (#95-01-36-11290). Animals were allotted to three groups (n = 8 in each group), and treated as follows: (i) Control (vehicle-treated); (ii) MnCl<sub>2</sub> (20 mg/mL in drinking water); and (iii) MnCl<sub>2</sub> (40 mg/mL in drinking water). Animals were treated for 42 consecutive days. On day 43, rats were anesthetized, and serum and kidney tissue samples were collected.</p></sec>
<sec id="S2_3">
<title>Sample collection</title>
<p>Animals were anesthetized (Thiopental 80 mg/kg, i.p). Blood was collected from the abdominal aorta and transferred to standard tubes (VACUSERA<sup>&#x00AE;</sup>, Serum gel, and clot activator tubes) for serum preparation. The kidney tissue was washed in ice-cooled (4&#x00B0;C) normal saline and used for further assessments. Kidney weight index (WI) was determined as WI = [wet weight of organ (g)/body weight (g)] &#x00D7; 100.</p></sec>
<sec id="S2_4">
<title>Reactive oxygen species</title>
<p>Renal tissue ROS levels were measured using dichlorofluorescein diacetate (DCFH-DA) as a fluorescent probe (<xref ref-type="bibr" rid="ref19">19</xref>). Briefly, 10 &#x03BC;L of DCFH-DA (10 &#x03BC;M final concentration) was added to 990 &#x03BC;L of tissue homogenate (10% w: v in KCl buffer). Samples were incubated for 15 min at 37&#x00B0;C in the dark. Finally, the DCF fluorescence intensity was assessed using a fluorimeter (FLUOstar Omega<sup>&#x00AE;</sup>, BMG LABTECH, Germany; &#x03BB;<sub>excit</sub> = 485 nm and &#x03BB;<sub>em</sub> = 525 nm) (<xref ref-type="bibr" rid="ref19">19</xref>).</p></sec>
<sec id="S2_5">
<title>Renal tissue lipid peroxidation</title>
<p>Thiobarbituric acid reactive substances (TBARS) in renal tissue were measured as an index of lipid peroxidation in the renal tissue (<xref ref-type="bibr" rid="ref12">12</xref>, <xref ref-type="bibr" rid="ref20">20</xref>). Briefly, renal tissue (500 mg) was homogenized in ice-cooled KCl buffer (1.15% w: v; 4&#x00B0;C). Then, 500 &#x00B5;L of tissue homogenate was added to a reaction mixture consisting of 1 mL TBA (0.375%, w: v), 1 mL trichloroacetic acid (20% w: v), and meta-phosphoric acid (3 mL f 1% w: v solution, pH = 2) (<xref ref-type="bibr" rid="ref21">21</xref>). The mixture was incubated in a water bath (100&#x00B0;C) for 45 min (<xref ref-type="bibr" rid="ref22">22</xref>). Then, 4 mL of n-butanol was added and vortexed (1 min). Finally, samples were centrifuged (17,000 &#x00D7; <italic>g</italic> for 10 min) and the absorbance of the developed color in upper phase (n-butanol) was measured at &#x03BB; = 532 nm (EPOCH<sup>&#x00AE;</sup> plate reader, Highland Park, USA) (<xref ref-type="bibr" rid="ref21">21</xref>).</p></sec>
<sec id="S2_6">
<title>Renal tissue and mitochondria glutathione content</title>
<p>Renal glutathione levels (oxidized and reduced; GSSG and GSH) were measured by the HPLC method (<xref ref-type="bibr" rid="ref23">23</xref>). The HPLC system consisted of an NH<sub>2</sub> column as the stationary phase (25 cm, Bischoff chromatography, Leonberg, Germany) (<xref ref-type="bibr" rid="ref24">24</xref>). The mobile phases consisted of buffer A (Water: Methanol; 1: 4 v: v) and buffer B (Acetate buffer: Buffer A; 1: 4 v: v), and a gradient method with a steady increase of buffer B to 95% in 25 min (<xref ref-type="bibr" rid="ref24">24</xref>). The flow rate of the mentioned mobile phase was 1 mL/min, and the UV detector (UV) detector was set at &#x03BB; = 254 nm. Tissue samples were homogenized in Tris-HCl buffer (250 mM; pH = 7.4; 4&#x00B0;C), and 500 &#x00B5;L of TCA (50% w: v) was added. Isolated mitochondria (1 mL, 1 mg protein/mL) were also treated with 100 &#x00B5;L of TCA 50% w: v. Samples were mixed well, incubated on ice (10 min), and centrifuged (17,000 g, 30 min, 4&#x00B0;C). Afterward, 1 mL of the supernatant was collected in 5 mL tubes and 300 &#x00B5;L of the NaOH: NaHCO<sub>3</sub> (2 M: 2 M) solution was added. Then, 100 &#x00B5;L of iodoacetic acid (1.5% w: v in deionized water) was added, and samples were incubated for 1 h (4&#x00B0;C, in the dark). Afterward, 2, 4-dinitrofluorobenzene (DNFB, 500 &#x00B5;L of 1.5% w: v in absolute ethanol) was added and mixed well. Samples were incubated in the dark (25&#x00B0;C, 24 h). Finally, samples were centrifuged (17,000 g, 30 min) and injected (25 &#x00B5;L) into the described HPLC system (<xref ref-type="bibr" rid="ref23">23</xref>).</p></sec>
<sec id="S2_7">
<title>Protein carbonylation</title>
<p>The oxidative damage of kidney tissue proteins was assessed based on the reaction with dinitrophenyl hydrazine (DNPH) (<xref ref-type="bibr" rid="ref25">25</xref>). Briefly, 1 mL of the tissue homogenate (10% w: v) was treated with 100 &#x00B5;L of the triton X-100 (0.1% w: v) and centrifuged (10 min, 700 g, 4&#x00B0;C). Then, 500 &#x00B5;L aliquots of the resulting supernatant were treated with 300 &#x00B5;L of DNPH (10 mM in HCl). Samples were then incubated for 1 h (25&#x00B0;C, vortexing every 10 min). Afterward, 100 &#x00B5;L of trichloroacetic acid (20% w: v) was added and centrifuged (12,000 g, 5 min) (26). The pellet was washed three times with ethanol: ethyl acetate (1 mL of 1: 1 v: v solution). Finally, the precipitate was re-dissolved in guanidine hydrochloride solution (600 &#x00B5;L of 6 M solution), and the absorbance at &#x03BB; = 370 nm was measured (EPOCH<sup>&#x00AE;</sup> plate reader, Highland Park, USA) (<xref ref-type="bibr" rid="ref25">25</xref>).</p></sec>
<sec id="S2_8">
<title>Ferric reducing antioxidant power</title>
<p>The ferric reducing antioxidant power (FRAP) of kidney tissue was measured (<xref ref-type="bibr" rid="ref27">27</xref>). The FRAP assay measures change in the absorbance at &#x03BB; = 593 nm due to the formation of a blue-colored ferrous (Fe<sup>2+</sup>)-4, 6-tripyridyl-s-triazine (TPTZ) complex from the colorless oxidized ferric form (Fe<sup>3+</sup>) by the action of tissue electron-donating antioxidants. The working FRAP solution was freshly prepared by mixing 25 mL of acetate buffer (300 mmol/L; pH = 3.6) with 2.5 mL of TPTZ ( 10 mmol/L in 40 mmol/L HCl) and 2.5 mL of ferric chloride (FeCl<sub>2</sub>, 20 mmol/L). Tissue samples (200 mg) were homogenized in 5 mL of 250 mM Tris-HCl buffer (pH = 7.4; 4&#x00B0;C). Afterward, 50 &#x00B5;L of tissue homogenate was added to 900 &#x00B5;L of the FRAP reagent and incubated in the dark (37&#x00B0;C, 5 min). The intensity of the resultant blue color was measured at &#x03BB; = 593 nm using an EPOCH plate reader (BioTek<sup>&#x00AE;</sup> Instruments, Highland Park, US) (<xref ref-type="bibr" rid="ref27">27</xref>).</p></sec>
<sec id="S2_9">
<title>Histopathological assessment</title>
<p>For histopathological evaluations, renal specimens were fixed in a buffered formalin solution prepared from NaH<sub>2</sub>PO<sub>4</sub> (0.4% w: v), Na<sub>2</sub>HPO<sub>4</sub> (0.64% w: v), and formaldehyde (10%) in double-distilled water (pH = 7.4). Paraffin-embedded tissue specimens were cut (5 &#x00B5;m) using a microtome and stained with hematoxylin and eosin. Kidney histopathological changes were evaluated using a light microscope (Olympus BX41; Olympus Optical Co. Ltd, Japan).</p></sec>
<sec id="S2_10">
<title>Renal and serum Mn levels</title>
<p>Serum and kidney Mn levels were measured using an inductively coupled plasma mass spectrometry (ICP-MS) method (<xref ref-type="bibr" rid="ref28">28</xref>). Briefly, serum (500 &#x00B5;L) and kidney tissue samples (500 &#x00B5;L of 10% w: v tissue homogenate) were treated with 100 &#x00B5;L of nitric acid (HNO<sub>3</sub>; 2.5% w: v) and centrifuged (17,000 g, 30 min). The supernatants were collected and used for Mn determination (<xref ref-type="bibr" rid="ref28">28</xref>).</p></sec>
<sec id="S2_11">
<title>Kidney mitochondria isolation</title>
<p>Rats&#x2019; kidneys were washed (NaCl 0.9% w: v, 4&#x00B0;C) and minced in the ice-cold isolation buffer containing 0.5 mM EGTA, 2 mM HEPES, 220 mM sucrose, 70 mM mannitol, and BSA (0.1% w: v) (pH = 7.4). Minced tissue was transported into fresh isolation buffer (5 mL buffer: 1 g tissue) and homogenized. Kidney mitochondria were isolated based on the differential centrifugation method (<xref ref-type="bibr" rid="ref29">29</xref>). For this purpose, unbroken cells and nuclei were pelleted at the first round of centrifugation (1000 <italic>g</italic> for 10 min at 4&#x00B0;C). Afterward, the supernatant was centrifuged at 10,000 <italic>g</italic> (10 min at 4&#x00B0;C) to pellet the mitochondria fraction (brown-colored). The second centrifugation step was repeated at least thrice using a fresh buffer medium. Finally, mitochondrial pellets were resuspended in a buffer (5 mL buffer/g tissue) containing 70 mM mannitol, 220 mM sucrose, and 2 mM HEPES (pH = 7.4). The mitochondria fractions used to measure mitochondrial permeabilization and mitochondrial depolarization were suspended in mitochondria permeabilization buffer (65 mM KCl, 10 mM HEPES, 125 mM Sucrose, pH = 7.2) and depolarization assay buffer (220 mM Sucrose, 10 mM KCl, 68 mM Mannitol, 5 mM KH<sub>2</sub>PO<sub>4</sub>, 2 mM MgCl<sub>2</sub>, 50 &#x03BC;M EGTA, and 10 mM HEPES, pH = 7.2) (<xref ref-type="bibr" rid="ref29">29</xref>). Sample protein concentrations were determined based on the Bradford method to standardize the obtained data.</p></sec>
<sec id="S2_12">
<title>Mitochondrial dehydrogenases activity</title>
<p>A colorimetric technique based on the production of purple formazan crystals from the 3-(4, 5-dimethylthiazol-2-yl)-2, 5-diphenyltetrazolium bromide was used for the estimation of mitochondrial dehydrogenases activity (<xref ref-type="bibr" rid="ref30">30</xref>). Briefly, a mitochondrial suspension (0.5 mg protein/mL) was incubated with 40 &#x00B5;L of MTT (0.4% w: v) and incubated in the dark (37&#x00B0;C, 30 min). Samples were centrifuged (15,000 g, 15 min), and the pellet was dissolved in dimethyl sulfoxide (DMSO; 1000 &#x00B5;L). The optical density (OD) at &#x03BB; = 570 nm was measured with an EPOCH<sup>&#x00AE;</sup> plate reader (Highland Park, USA) (<xref ref-type="bibr" rid="ref30">30</xref>).</p></sec>
<sec id="S2_13">
<title>Mitochondrial ATP levels</title>
<p>Based on a previously reported protocol, mitochondrial ATP level was assessed by HPLC (<xref ref-type="bibr" rid="ref31">31</xref>, <xref ref-type="bibr" rid="ref32">32</xref>). Briefly, isolated mitochondria (1 mg protein/mL) were mixed with 100 &#x00B5;L ice-cooled meta-phosphoric acid solution (50% w: v, 4&#x00B0;C) and centrifuged (30 min, 17,000 <italic>g</italic>, 4&#x00B0;C). Afterward, the supernatant (100 &#x00B5;L) was treated with 15 &#x00B5;L of ice-cooled potassium hydroxide solution (KOH, 1 M). Samples were centrifuged (30 min, 17,000 <italic>g</italic>, 4&#x00B0;C) again, and 25 &#x00B5;L of the supernatant was injected into an HPLC system composed of an LC-18 column (&#x00B5;-Bondapak, 25 cm). The mobile phase was composed of potassium hydrogen phosphate mono-basic (100 mM KH<sub>2</sub>PO<sub>4</sub>, pH = 7 adjusted with KOH), acetonitrile (2.5% v: v), and tetrabutylammonium hydroxide (1 mM). The flow rate was 1 mL/min, and the UV detector was set at &#x03BB; = 254 nm (<xref ref-type="bibr" rid="ref31">31</xref>).</p></sec>
<sec id="S2_14">
<title>Mitochondrial depolarization</title>
<p>Mitochondrial uptake of the cationic dye rhodamine 123 was applied for the evaluation of mitochondrial depolarization (<xref ref-type="bibr" rid="ref33">33</xref>, <xref ref-type="bibr" rid="ref34">34</xref>). Rhodamine 123 accumulates in the mitochondrial matrix by facilitated diffusion. When the mitochondrion is depolarized, there is no facilitated diffusion, and the amount of rhodamine 123 in the supernatant will be increased (<xref ref-type="bibr" rid="ref35">35</xref>). In the current investigation, the mitochondrial fractions (0.5 mg protein/mL; in the depolarization assay buffer) were incubated with 10 &#x00B5;M of rhodamine 123 (30 min, 37&#x00B0;C, in the dark). Afterward, samples were centrifuged (15,000 g, 10 min, 4&#x00B0;C) and the fluorescence intensity of the supernatant was monitored with a fluorimeter (FLUOstar Omega<sup>&#x00AE;</sup>; BMG, Germany; &#x03BB;<sub>excit</sub> = 485 nm and &#x03BB;<sub>em</sub> = 525 nm) (<xref ref-type="bibr" rid="ref33">33</xref>, <xref ref-type="bibr" rid="ref36">36</xref>).</p></sec>
<sec id="S2_15">
<title>Mitochondrial permeabilization and swelling</title>
<p>Mitochondrial swelling was estimated by analyzing the changes in optical density at &#x03BB; = 540 nm (<xref ref-type="bibr" rid="ref34">34</xref>, <xref ref-type="bibr" rid="ref37">37</xref>). Briefly, isolated mitochondria (0.5 mg protein/ml) were suspended in the mitochondria permeabilization buffer (65 mM KCl, 125 mM Sucrose, 10 mM HEPES, pH = 7.2), and the absorbance was monitored (30&#x00B0;C, during 30 min of incubation) using an EPOCH<sup>&#x00AE;</sup> plate reader (Highland Park, USA). An increase in mitochondrial swelling is associated with a decrease in absorbance. The results are reported as maximal mitochondrial swelling amplitude (&#x0394;OD 540 nm) (<xref ref-type="bibr" rid="ref37">37</xref>).</p></sec>
<sec id="S2_16">
<title>Lipid peroxidation in kidney mitochondria</title>
<p>TBARS were measured in isolated kidney mitochondria. Previous studies mentioned that sucrose interferes with the lipid peroxidation test in isolated mitochondria preparations (<xref ref-type="bibr" rid="ref37">37</xref>). Therefore, mitochondria preparations were washed once (to remove sucrose) in ice-cooled MOPS-KCl buffer (100 mM KCl, 50 mM MOPS, 4&#x00B0;C, pH = 7.4). For this purpose, isolated kidney mitochondria were suspended in 5 mL of MOPS-KCl buffer and centrifuged (15,000 g, 4&#x00B0;C, 20 min). The pellet was re-suspended in MOPS-KCl buffer and used for TBARs assay. The mitochondrial suspension (1 mg protein/mL) was mixed with 1 mL of a solution containing trichloroacetic acid (15% w: v), HCl (0.24 N), TBA (0.375% w: v), and Trolox (500 &#x00B5;M). Samples were heated for 15 min at 100&#x00B0;C (<xref ref-type="bibr" rid="ref37">37</xref>). Then n-butanol (1 mL) was added and vortexed (5 min). Samples were centrifuged (15,000 <italic>g</italic>, 10 min), and the absorbance of the n-butanol phase (upper phase) was measured (EPOCH<sup>&#x00AE;</sup> plate reader, Highland Park, USA, &#x03BB; = 532 nm) (<xref ref-type="bibr" rid="ref37">37</xref>).</p></sec>
<sec id="S2_17">
<title>Statistical methods</title>
<p>Data are represented as mean &#x00B1; SD. Data analysis was accomplished by the one-way analysis of variance (ANOVA) and the Tukey&#x2019;s multiple comparison test as the <italic>post hoc</italic> test. A P &#x003C; 0.05 was considered as a statistically significant difference.</p></sec>
</sec>
<sec id="S3" sec-type="results">
<title>Results</title>
<p>Animal weight gain was significantly lower in the Mn-treated group (40 mg/mL) in comparison with control rats (<xref ref-type="fig" rid="F1">Figure 1A</xref>). The kidney WI was also significantly lower in Mn 40 mg/mL group (<xref ref-type="fig" rid="F1">Figure 1A</xref>). Serum and kidney tissue Mn levels were also significantly higher in Mn-treated animals (<xref ref-type="fig" rid="F1">Figure 1B</xref>).</p>
<fig id="F1" orientation="portrait" position="float">
<label>Figure 1.</label>
<caption><p>Effect of manganese treatment (20 and 40 mg/mL for 30 consecutive days) on animals&#x2019; weight gain, renal weight index (Panel A), and serum and kidney tissue manganese (Mn) (Panel B).</p>
<p>Data are shown as mean &#x00B1; SD (n = 8).</p>
<p><sup>#</sup>Indicates significantly different as compared with the control group (P &#x003C; 0.05).</p></caption>
<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="https://jrenhep.com/article/download/66/version/45/128/851/JRENHEP-4-001-g001.jpg"/>
</fig>
<p>Significant deterioration in serum biochemical measurements indicates renal injury in Mn-treated rats (<xref ref-type="table" rid="T1">Table 1</xref>). Signs of hypophosphatemia were evident in the Mn group (<xref ref-type="table" rid="T1">Table 1</xref>). On the other hand, serum BUN and creatinine levels were significantly higher in Mn-exposed animals (20 and 40 mg/mL) (<xref ref-type="table" rid="T1">Table 1</xref>). Significant elevation in urine protein, alkaline phosphatase (ALP), &#x03B3;-glutamyl transferase (&#x03B3;-GT), and glucose level was also detected in Mn-treated rats (<xref ref-type="table" rid="T2">Table 2</xref>).</p>
<table-wrap id="T1" orientation="portrait" position="float">
<label>Table 1.</label><caption><p>Serum biochemical measurements in manganese (Mn)-treated rats.</p></caption>
<table frame="border" rules="all">
<thead valign="top">
<tr>
<th></th>
<th align="center">Control</th>
<th align="center">Mn<break/>20 mg/mL</th>
<th align="center">Mn<break/>40 mg/mL</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td>Ca<sup>2+</sup> (mg/dL)</td>
<td align="center">5.0 &#x00B1; 0.20</td>
<td align="center">4.9 &#x00B1; 0.40</td>
<td align="center">5.0 &#x00B1; 0.50</td>
</tr>
<tr>
<td>K<sup>+</sup> (mmol/L)</td>
<td align="center">5.5 &#x00B1; 0.40</td>
<td align="center">4.6 &#x00B1; 0.32</td>
<td align="center">4.5 &#x00B1; 0.50</td>
</tr>
<tr>
<td>Na<sup>+</sup> (mmol/L)</td>
<td align="center">84.0 &#x00B1; 4.00</td>
<td align="center">76 &#x00B1; 3.00</td>
<td align="center">71.0 &#x00B1; 2.00</td>
</tr>
<tr>
<td>Glucose (mg/dL)</td>
<td align="center">113.0 &#x00B1; 9.00</td>
<td align="center">105 &#x00B1; 5.00</td>
<td align="center">97.0 &#x00B1; 11.00</td>
</tr>
<tr>
<td>Phosphate (mg/dL)</td>
<td align="center">3.4 &#x00B1; 0.40</td>
<td align="center">2.33 &#x00B1; 0.40</td>
<td align="center">2.1 &#x00B1; 0.11<sup>#</sup></td>
</tr>
<tr>
<td>Total protein (mg/dL)</td>
<td align="center">6.8 &#x00B1; 0.44</td>
<td align="center">7.1 &#x00B1; 0.9</td>
<td align="center">6.9 &#x00B1; 0.30</td>
</tr>
<tr>
<td>Blood urea nitrogen (mg/dL)</td>
<td align="center">43.0 &#x00B1; 2.00</td>
<td align="center">66.0 &#x00B1; 5.00<sup>#</sup></td>
<td align="center">68 &#x00B1; 4.00<sup>#</sup></td>
</tr>
<tr>
<td>Creatinine (mg/dL)</td>
<td align="center">0.3 &#x00B1; 0.02</td>
<td align="center">0.6 &#x00B1; 0.03<sup>#</sup></td>
<td align="center">0.8 &#x00B1; 0.03<sup>#</sup></td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="TF1-1"><p>Data are represented as mean &#x00B1; SD (n = 8).</p>
<p><sup>#</sup>Indicates significantly different as compared with the control group (P &#x003C; 0.01).</p></fn></table-wrap-foot>
</table-wrap>
<table-wrap id="T2" orientation="portrait" position="float">
<label>Table 2.</label><caption><p>Urinalysis of manganese (Mn)-treated animals</p></caption>
<table frame="border" rules="all">
<thead valign="top">
<tr>
<th></th>
<th align="center">Control</th>
<th align="center">Mn<break/>20 mg/mL</th>
<th align="center">Mn<break/>40 mg/mL</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td>Protein (mg/dL)</td>
<td align="center">0.4 &#x00B1; 0.1</td>
<td align="center">1.1 &#x00B1; 0.10<sup>#</sup></td>
<td align="center">1.2 &#x00B1; 0.20<sup>#</sup></td>
</tr>
<tr>
<td>ALP (U/L)</td>
<td align="center">2122 &#x00B1; 115</td>
<td align="center">2380 &#x00B1; 193</td>
<td align="center">2670 &#x00B1; 390<sup>#</sup></td>
</tr>
<tr>
<td>&#x03B3;-GT (U/L)</td>
<td align="center">2569 &#x00B1; 166</td>
<td align="center">3134 &#x00B1; 113</td>
<td align="center">3897 &#x00B1; 575<sup>#</sup></td>
</tr>
<tr>
<td>Glucose (mg/dL)</td>
<td align="center">80.0 &#x00B1; 4.00</td>
<td align="center">96.0 &#x00B1; 19.00</td>
<td align="center">132.0 &#x00B1; 3.00<sup>#</sup></td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="TF2-1"><p>Data are represented as mean &#x00B1; SD (n = 8).</p>
<p>ALP: alkaline phosphatase; &#x03B3;-GT: &#x03B3;-glutamyl transferase.</p>
<p><sup>#</sup>Indicates significantly different as compared with the control group (P &#x003C; 0.01)</p></fn></table-wrap-foot>
</table-wrap>
<p>Significant ROS formation, lipid peroxidation, and protein carbonylation were detected in Mn groups (<xref ref-type="fig" rid="F2">Figure 2</xref>). Moreover, kidney tissue GSH was depleted, and the GSSG level was significantly increased in Mn-exposed animals (<xref ref-type="fig" rid="F2">Figure 2</xref>). Tissue antioxidant capacity was also dose-dependently decreased in the kidneys of Mn-treated rats (<xref ref-type="fig" rid="F2">Figure 2</xref>).</p>
<fig id="F2" orientation="portrait" position="float">
<label>Figure 2.</label>
<caption><p>Markers of oxidative stress in the kidney tissue of manganese-treated rats.</p>
<p>Data are given as mean &#x00B1; SD (n = 8).</p>
<p>Asterisks indicate significantly different from the control group (* P &#x003C; 0.05, *** P &#x003C; 0.001).</p></caption>
<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="https://jrenhep.com/article/download/66/version/45/128/852/JRENHEP-4-001-g002.jpg"/>
</fig>
<p>Several mitochondrial indices were assessed in the kidney tissue of Mn-treated rats (<xref ref-type="fig" rid="F3">Figure 3</xref>). It was found that Mn exposure significantly decreased mitochondrial dehydrogenases activity and ATP levels in a dose-dependent manner (<xref ref-type="fig" rid="F3">Figure 3</xref>). Moreover, a significant increment of mitochondrial depolarization and swelling was detected in the kidney mitochondria of Mn-treated animals (<xref ref-type="fig" rid="F3">Figure 3</xref>). Lipid peroxidation was also dose-dependently increased in the kidney mitochondria isolated from Mn-exposed animals (<xref ref-type="fig" rid="F3">Figure 3</xref>).</p>
<fig id="F3" orientation="portrait" position="float">
<label>Figure 3.</label>
<caption><p>Markers of mitochondrial impairment in the kidneys of manganese-treated animals.</p>
<p>Data are presented as mean &#x00B1; SD (n = 8).</p>
<p>*** Significantly different from the control group (P &#x003C; 0.001).</p></caption>
<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="https://jrenhep.com/article/download/66/version/45/128/853/JRENHEP-4-001-g003.jpg"/>
</fig>
<p>Significant interstitial inflammation and tubular atrophy were evident in the kidneys of Mn 20 and 40 mg/mL groups (<xref ref-type="fig" rid="F4">Figure 4</xref> and <xref ref-type="table" rid="T3">Table 3</xref>). Moreover, Mn 40 mg/mL caused renal tissue necrosis (<xref ref-type="fig" rid="F4">Figure 4</xref> and <xref ref-type="table" rid="T3">Table 3</xref>).</p>
<fig id="F4" orientation="portrait" position="float">
<label>Figure 4.</label>
<caption><p>Kidney tissue histopathological alterations in manganese-exposed animals. Hematoxylin and eosin staining. The grades of histopathological changes are given in <xref ref-type="table" rid="T3">Table 3</xref>.</p></caption>
<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="https://jrenhep.com/article/download/66/version/45/128/854/JRENHEP-4-001-g004.jpg"/>
</fig>
<table-wrap id="T3" orientation="portrait" position="float">
<label>Table 3.</label><caption><p>Renal tissue histopathological alterations in manganese-exposed rats.</p></caption>
<table frame="border" rules="all">
<thead valign="top">
<tr>
<th></th>
<th align="center">Interstitial inflammation</th>
<th align="center">Tubular atrophy</th>
<th align="center">Necrosis</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td>Control</td> 
<td align="center">&#x2212;</td>
<td align="center">&#x2212;</td>
<td align="center">&#x2212;</td>
</tr>
<tr>
<td>Manganese 20 mg/mL</td>
<td align="center">+</td>
<td align="center">+</td>
<td align="center">+</td>
</tr>
<tr>
<td>Manganese 40 mg/mL</td>
<td align="center">++</td>
<td align="center">++</td>
<td align="center">+++</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="TF3-1"><p>+: Mild; ++: Moderate; and +++: Severe histopathological alterations.</p></fn></table-wrap-foot>
</table-wrap>
</sec>
<sec id="S4" sec-type="discussion">
<title>Discussion</title>
<p>Mn is a trace element that plays a fundamental role in several metabolic pathways and enzyme structures (<xref ref-type="bibr" rid="ref2">2</xref>). However, overexposure to this metal is associated with a wide range of adverse effects, including renal injury (<xref ref-type="bibr" rid="ref6">6</xref>&#x2013;<xref ref-type="bibr" rid="ref8">8</xref>, <xref ref-type="bibr" rid="ref38">38</xref>). Acute tubular necrosis, proteinuria, oliguria, and significant elevation in serum creatinine levels have been reported in human cases of Mn-induced nephrotoxicity (<xref ref-type="bibr" rid="ref6">6</xref>, <xref ref-type="bibr" rid="ref38">38</xref>&#x2013;<xref ref-type="bibr" rid="ref40">40</xref>). No precise mechanism for Mn-induced nephrotoxicity has been identified so far. In the current investigation, it was found that Mn caused significant oxidative stress as well as mitochondrial impairment in the kidney tissue. The results might help in the development of therapeutic options against renal failure and serum electrolyte imbalance observed in Mn-intoxicated patients (<xref ref-type="bibr" rid="ref6">6</xref>, <xref ref-type="bibr" rid="ref38">38</xref>&#x2013;<xref ref-type="bibr" rid="ref41">41</xref>).</p>
<p>Neurotoxicity is a well-described adverse effect of Mn (<xref ref-type="bibr" rid="ref9">9</xref>, <xref ref-type="bibr" rid="ref13">13</xref>, <xref ref-type="bibr" rid="ref42">42</xref>&#x2013;<xref ref-type="bibr" rid="ref45">45</xref>). Oxidative stress and its consequences, such as disruption of biomembrane lipids and protein carbonylation, seem to play a fundamental role in Mn-induced toxicity in different organs such as the brain (<xref ref-type="bibr" rid="ref9">9</xref>, <xref ref-type="bibr" rid="ref13">13</xref>, <xref ref-type="bibr" rid="ref42">42</xref>&#x2013;<xref ref-type="bibr" rid="ref45">45</xref>). Severe elevation in brain tissue ROS level and lipid peroxidation has been documented in Mn-induced neurotoxicity (<xref ref-type="bibr" rid="ref9">9</xref>, <xref ref-type="bibr" rid="ref13">13</xref>, <xref ref-type="bibr" rid="ref42">42</xref>&#x2013;<xref ref-type="bibr" rid="ref45">45</xref>). Moreover, it has been found that brain tissue antioxidant systems are hampered upon Mn overexposure (<xref ref-type="bibr" rid="ref9">9</xref>, <xref ref-type="bibr" rid="ref13">13</xref>, <xref ref-type="bibr" rid="ref42">42</xref>&#x2013;<xref ref-type="bibr" rid="ref45">45</xref>). The mechanism(s) of nephrotoxicity induced by Mn is less understood. Previous studies mentioned the occurrence of oxidative stress in the renal tissue of Mn-exposed animals (<xref ref-type="bibr" rid="ref7">7</xref>). Mn-induced oxidative stress could affect several cellular targets, including biomembrane lipids, proteins, as well as deoxyribonucleic acid (<xref ref-type="bibr" rid="ref7">7</xref>). In the current study, significant ROS formation, protein carbonylation, lipid peroxidation, and depletion of kidney tissue antioxidant capacity was evident in Mn-exposed rats. These results are consistent with previous investigations indicating Mn-induced oxidative stress in the kidney (<xref ref-type="bibr" rid="ref7">7</xref>). Moreover, we found that kidney mitochondria could also be affected by Mn overexposure.</p>
<p>Cellular mitochondria are critical targets affected by Mn. (<xref ref-type="bibr" rid="ref13">13</xref>). It has been found that Mn is accumulated in the mitochondrial matrix through Ca<sup>2+</sup> channels (<xref ref-type="bibr" rid="ref13">13</xref>). Induction of mitochondrial permeabilization, enhancement of mitochondria-facilitated ROS formation, a decrease of cellular ATP levels, and mitochondria-mediated cell death and apoptosis are associated with Mn-induced mitochondrial impairment (<xref ref-type="bibr" rid="ref13">13</xref>).</p>
<p>Mitochondria play a fundamental role in kidney tissue (<xref ref-type="bibr" rid="ref14">14</xref>&#x2013;<xref ref-type="bibr" rid="ref16">16</xref>). The reabsorption of chemicals (e.g., amino acids, glucose, and minerals) from nephrons to the bloodstream is an energy-dependent activity (<xref ref-type="bibr" rid="ref14">14</xref>&#x2013;<xref ref-type="bibr" rid="ref16">16</xref>). Kidney tissue contains numerous mitochondria, the proper functioning of which guarantee enough ATP required for the reabsorption process of chemicals (<xref ref-type="bibr" rid="ref14">14</xref>&#x2013;<xref ref-type="bibr" rid="ref16">16</xref>). Hence, Mn-induced mitochondrial impairment leads to an energy crisis and defect in the reabsorption of many chemicals in the renal tubules. Consequently, serum electrolyte disturbances could occur. Cellular mitochondria are also important sites of ROS production (<xref ref-type="bibr" rid="ref18">18</xref>). It has been repeatedly reported that xenobiotics-induced mitochondrial impairment could facilitate mitochondria-mediated ROS formation (<xref ref-type="bibr" rid="ref18">18</xref>). Based on the data obtained from the current study, we might be able to speculate that Mn-induced mitotoxicity could serve as a major cause of oxidative stress in the renal tissue.</p></sec>
<sec id="S5" sec-type="conclusions">
<title>Conclusion</title>
<p>Collectively, our results indicate the fundamental role of oxidative stress and mitochondrial impairment in the pathogenesis of Mn-induced renal injury. Therefore, targeting cellular mitochondria might serve as a therapeutic point against Mn-induced nephrotoxicity.</p></sec>
</body>
<back>
<ack>
<title>Acknowledgments</title>
<p>This investigation was financially supported by the Vice-Chancellor of Research Affairs of Shiraz University of Medical Sciences (17782/17660). Authors acknowledge the Pharmaceutical Sciences Research Center of Shiraz University of Medical Sciences for providing technical facilities to carry out this study.</p>
<sec id="S6" sec-type="COI-statement">
<title>Conflict of interest</title>
<p>The authors declare that there are no conflicts of interest.</p></sec>
</ack>
<fn-group>
<fn id="fn1"><p><italic>How to cite</italic>: Niknahad AM, et al. Manganese-Induced Nephrotoxicity is Mediated through Oxidative Stress and Mitochondrial Impairment. J Ren Hepat Disord. 2020;4(2):1&#x2013;10.</p></fn></fn-group>
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