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<art><ui>1746-1448-6-6</ui><ji>1746-1448</ji><fm>
<dochead>Short Report</dochead>
<bibl>
<title>
<p>Characterization of manganese superoxide dismutase from a marine cyanobacterium <it>Leptolyngbya valderiana </it>BDU20041</p>
</title>
<aug>
<au id="A1" ce="yes"><snm>Priya</snm><fnm>Balakrishnan</fnm><insr iid="I1"/><email>priya.bkrishnan@gmail.com</email></au>
<au id="A2" ce="yes"><snm>Sivaprasanth</snm><mi>K</mi><fnm>Reddi</fnm><insr iid="I2"/><email>reddisiva@gmail.com</email></au>
<au id="A3"><snm>Jensi</snm><mnm>Dhivya</mnm><fnm>Vincent</fnm><insr iid="I1"/><email>dhivya.nfmc@gmail.com</email></au>
<au id="A4"><snm>Uma</snm><fnm>Lakshmanan</fnm><insr iid="I1"/><email>lumaprabakar@yahoo.com</email></au>
<au id="A5"><snm>Subramanian</snm><fnm>Gopalakrishnan</fnm><insr iid="I1"/><email>gs@subramanians.net</email></au>
<au ca="yes" id="A6"><snm>Prabaharan</snm><fnm>Dharmar</fnm><insr iid="I1"/><email>dharmarpraba@yahoo.com</email></au>
</aug>
<insg>
<ins id="I1"><p>National Facility for Marine Cyanobacteria (Sponsored by Dept. of Biotechnology, Govt. of India), Department of Marine Biotechnology, School of Marine Sciences, Bharathidasan University, Tiruchirappalli, Tamil Nadu, India</p></ins>
<ins id="I2"><p>Graduate Institute of Biotechnology, National Chung Hsing University, 250, Kuo-Kuang Road, Taichung, Taiwan</p></ins>
</insg>
<source>Saline Systems</source>
<issn>1746-1448</issn>
<pubdate>2010</pubdate>
<volume>6</volume>
<issue>1</issue>
<fpage>6</fpage>
<url>http://www.salinesystems.org/content/6/1/6</url>
<xrefbib><pubidlist><pubid idtype="pmpid">20525290</pubid><pubid idtype="doi">10.1186/1746-1448-6-6</pubid></pubidlist></xrefbib>
</bibl>
<history><rec><date><day>29</day><month>11</month><year>2009</year></date></rec><acc><date><day>3</day><month>6</month><year>2010</year></date></acc><pub><date><day>3</day><month>6</month><year>2010</year></date></pub></history>
<cpyrt><year>2010</year><collab>Priya et al; licensee BioMed Central Ltd.</collab><note>This is an Open Access article distributed under the terms of the Creative Commons Attribution License (<url>http://creativecommons.org/licenses/by/2.0</url>), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.</note></cpyrt>
<abs>
<sec>
<st>
<p>Abstract</p>
</st>
<sec>
<st>
<p>Background</p>
</st>
<p>Cyanobacteria are recognized as the primordial organisms to grace the earth with molecular oxygen ~3.5 billion years ago as a result of their oxygenic photosynthesis. This laid a selection pressure for the evolution of antioxidative defense mechanisms to alleviate the toxic effect of active oxygen species (AOS) in cyanobacteria. Superoxide dismutases (SODs) are metalloenzymes that are the first arsenal in defense mechanism against oxidative stress followed by an array of antioxidative system. Unlike other living organisms, cyanobacteria possess multiple isoforms of SOD. Hence, an attempt was made to demonstrate the oxidative stress tolerance ability of marine cyanobacterium, <it>Leptolyngbya valderiana </it>BDU 20041 and to PCR amplify and sequence the SOD gene, the central enzyme for alleviating stress.</p>
</sec>
<sec>
<st>
<p>Result</p>
</st>
<p>
<it>L. valderiana </it>BDU 20041, a filamentous, non-heterocystous marine cyanobacterium showed tolerance to the tested dye (C.I. Acid Black 1) which is evident by increased in biomass (i.e.) chlorophyll <it>a</it>. The other noticeable change was the total ROS production by culture dosed with dye compared to the control cultures. This prolonged incubation showed sustenance, implying that cyanobacteria maintain their antioxidant levels. The third significant feature was a two-fold increase in SOD activity of dye treated <it>L. valderiana </it>BDU20041 suggesting the role of SOD in alleviating oxidative stress <it>via </it>Asada-Halliwell pathway. Hence, the organism was PCR amplified for SOD gene resulting in an amplicon of 550 <it>bp</it>. The sequence analysis illustrated the presence of first three residues involved in motif; active site residues at H4, 58 and D141 along with highly conserved Mn specific residues. The isolated gene shared 63.8% homology with MnSOD of bacteria confirmed it as Mn isoform. This is the <it>hitherto </it>report on SOD gene from marine cyanobacterium, <it>L. valderiana </it>BDU20041 of Indian subcontinent.</p>
</sec>
<sec>
<st>
<p>Conclusion</p>
</st>
<p>Generation of Reactive Oxygen Species (ROS) coupled with induction of SOD by marine cyanobacterium, <it>L. valderiana </it>BDU20041 was responsible for alleviating stress caused by an azo dye, C. I. Acid Black 1. The partial SOD gene has been sequenced and based on the active site, motif and metal specific residues; it has been identified as Mn metalloform.</p>
</sec>
</sec>
</abs>
</fm><bdy>
<sec>
<st>
<p>Introduction</p>
</st>
<p>Cyanobacteria, the oxygen-evolving photosynthetic prokaryote originated ~3.5 billion years ago, occupy a credential position between pro- and eukaryotes <abbrgrp>
<abbr bid="B1">1</abbr>
</abbrgrp>. The resultant tandem operation of two photosystems is now known as oxygenic or plant-type photosynthesis <abbrgrp>
<abbr bid="B1">1</abbr>
</abbrgrp>. This marked the turning point in the evolution of earth, opening up the era for aerobes. For the survival of cyanobacteria with oxygenic photosynthesis, the selection pressure led to the evolution of SODs <abbrgrp>
<abbr bid="B2">2</abbr>
<abbr bid="B3">3</abbr>
<abbr bid="B4">4</abbr>
<abbr bid="B5">5</abbr>
<abbr bid="B6">6</abbr>
<abbr bid="B7">7</abbr>
</abbrgrp>. Cyanobacteria are well documented for its ability to maintain the antioxidant levels by releasing H<sub>2</sub>O<sub>2 </sub>into the environment <abbrgrp>
<abbr bid="B2">2</abbr>
<abbr bid="B3">3</abbr>
<abbr bid="B4">4</abbr>
<abbr bid="B5">5</abbr>
</abbrgrp>. The prime armory for the release of H<sub>2</sub>O<sub>2 </sub>is superoxide dismutases. The first implication on the protective role of cyanobacterial SOD in photo-oxidative damage was shown in <it>Anacystis nidulans </it>
<abbrgrp>
<abbr bid="B6">6</abbr>
</abbrgrp>.</p>
<p>SODs are generally classified according to their metal species which acts as redox-active center to catalyze the dismutation reaction O<sub>2</sub>
<sup>- </sup>+ 2H<sup>+ </sup>&#8594; O<sub>2 </sub>+ H<sub>2</sub>O<sub>2</sub>. Cu/ZnSOD type consists of Cu(II) and Zn(II) at the active site, MnSOD has Mn(III), the third FeSOD possess Fe(III), and a fourth NiSOD contains Ni(II/III). Generally SODs are localization specific. MnSOD is found in the cytosol and thylakoid membrane, whereas Fe and NiSOD in the cytosol and Cu/Zn is periplasmic in location but cyanobacteria have multiple forms of each type encoded by more than one gene <abbrgrp>
<abbr bid="B7">7</abbr>
</abbrgrp>. The existence of multiple SODs may result from the fact that the cells of cyanobacteria are divided into compartments by internal membranes <abbrgrp>
<abbr bid="B8">8</abbr>
</abbrgrp>. Since O<sub>2</sub>
<sup>- </sup>ions are negatively charged and cannot cross the phospholipids bilayer readily, they are efficiently trapped within the compartment where they are generated. This may have been selected for the evolution of multiple SODs in compartmentalized cells <abbrgrp>
<abbr bid="B9">9</abbr>
</abbrgrp>.</p>
<p>Different levels of expressions in terms of SOD isoenzymes resulted in response to oxidative stress caused by various abiotic factors such as, pesticides <abbrgrp>
<abbr bid="B10">10</abbr>
</abbrgrp>, lignin and its model dye <abbrgrp>
<abbr bid="B11">11</abbr>
</abbrgrp> and nutrient limitation <abbrgrp>
<abbr bid="B12">12</abbr>
</abbrgrp> particularly of Fe/MnSOD. In addition, our <it>hitherto </it>reports on marine cyanobacterium, <it>Leptolyngbya valderiana </it>BDU 20041 on exposure to synthetic dye has shown that the organism decolourized Acid black1, C.I. 20470 (100 mG L<sup>-1</sup>) to 85.6% in 12 days <abbrgrp>
<abbr bid="B13">13</abbr>
<abbr bid="B14">14</abbr>
</abbrgrp>. The active moiety involved in decolourization was adjudged to be AOS, mainly H<sub>2</sub>O<sub>2 </sub>(40 &#956;M of H<sub>2</sub>O<sub>2 </sub>mG<sup>-1 </sup>Chl h<sup>-1</sup>) which is excreted by the organism into the <it>milieu </it>
<abbrgrp>
<abbr bid="B14">14</abbr>
</abbrgrp>. The SOD activity was found to be induced by two-fold in the presence of dye suggesting a significant role in the production of H<sub>2</sub>O<sub>2 </sub>
<abbrgrp>
<abbr bid="B14">14</abbr>
</abbrgrp>.</p>
<p>In the present study, we proposed to analyze the role of SOD in <it>L. valderiana </it>BDU 20041 during oxidative stress at the molecular level in order to more precisely identify its isoform. Hence, an attempt was made to PCR amplify, sequence and identify the metalloform of the SOD from the marine cyanobacterium, <it>L. valderiana </it>BDU20041 of Indian subcontinent.</p>
</sec>
<sec>
<st>
<p>Results and Discussions</p>
</st>
<p>ROS are repeatedly reported to be the inevitable by-products of biological redox reaction and normal metabolism in humans, animals, plants and algae <abbrgrp>
<abbr bid="B15">15</abbr>
</abbrgrp>. Cyanobacteria are oxygenic photosynthetic organisms that are prone to the oxidative stress due to the facts that they contain an array of photosynthetic pigments and that they both produce oxygen during photosynthesis and consume oxygen during respiration. It has been estimated that 1% of O<sub>2 </sub>consumed by cells is diverted to produce ROS in various subcellular loci <abbrgrp>
<abbr bid="B16">16</abbr>
</abbrgrp>.</p>
<p>The increased production of ROS and the resultant oxidative stress are considered to be the initial event and act as an alert signal for the organisms under several environmental stresses, such as light, temperature and UV. Inevitably, ROS also react with biologically important molecules such as lipids, proteins and DNA, inducing oxidative damage in membranes and the photosynthetic apparatus, which probably results in the death of cells <abbrgrp>
<abbr bid="B15">15</abbr>
</abbrgrp>. Here we focus on synthetic dye induced oxidative stress and oxidative damage in cyanobacteria.</p>
<p>In the present study, the dye dosed stress response of <it>L. valderiana </it>BDU20041 was tested in nitrogen free ASN III medium for a stipulated period of 12 days. The response to stress was determined by the organism's decolourizing efficiency which varied among the duration tested (Figure <figr fid="F1">1</figr>). This shows that decolourization was only due to the metabolic activity of the organisms and not an abiotic factor. The results compliance with the decolourization studies by cyanobacteria <abbrgrp>
<abbr bid="B17">17</abbr>
<abbr bid="B18">18</abbr>
</abbrgrp>.</p>
<fig id="F1"><title><p>Figure 1</p></title><caption><p>Rate of decolourization of C.I. Acid Black 1 (100 mG L<sup>-1</sup>) by <it>L. valderiana </it>BDU20041 in ASN III nitrogen free medium</p></caption><text>
   <p><b>Rate of decolourization of C.I. Acid Black 1 (100 mG L<sup>-1</sup>) by <it>L. valderiana </it>BDU20041 in ASN III nitrogen free medium</b>.</p>
</text><graphic file="1746-1448-6-6-1" hint_layout="single"/></fig>
<p>Earlier reports deciphers that oxidative stress induces formation of ROS by multiple pathways <abbrgrp>
<abbr bid="B15">15</abbr>
<abbr bid="B19">19</abbr>
</abbrgrp>. Firstly, the photosynthetic pigments such as chlorophylls and phycobilins in cyanobacteria that act as photosensitizers (PS) under stress <abbrgrp>
<abbr bid="B15">15</abbr>
</abbrgrp>. It is noteworthy that the energy of excited chlorophylls or phycobilins is utilized efficiently for photosynthesis under normal growth conditions. However, the inhibition of photosynthesis or the electron transport chain under stress may elevate the photosensitization process as well as the formation of ROS in this way.</p>
<p>Secondly, the essential role of the photosynthetic electron transport chain in the life of cyanobacteria promotes the possibility of subjection to oxidative stress. The probable electron transfer from the electron transport chain, especially in photosystem I (PSI), to molecular oxygen, the way to quench extensive excitation energy, is an alternative source of ROS. Photoreduction of molecular oxygen by the primary electron acceptor in the PSI complex is thought to be the main source of superoxide in illuminated cells <abbrgrp>
<abbr bid="B19">19</abbr>
</abbrgrp>.</p>
<p>Hence in the present study, experiments were carried out to evaluate the above phenomena as a response of <it>L. valderiana </it>BDU20041 to oxidative stress caused by C.I. Acid Black 1.</p>
<p>First, dye treated <it>L. valderiana </it>BDU20041 showed increase in chlorophyll <it>a </it>proportional to the rate of decolourization (Figure <figr fid="F2">2</figr>) which suggests that dye hinders the availability of light for the photosynthetic machinery. In addition, there was a slight variation in the phycobilins of dye untreated and treated <it>L. valderiana </it>BDU20041 at the end of 12 days (Figure <figr fid="F3">3</figr>). These changes in chlorophyll and phycobilins during decolourization corroborate with the first phenomena mentioned above on the organism's potential to strive against oxidative stress caused by C.I. Acid Black 1.</p>
<fig id="F2"><title><p>Figure 2</p></title><caption><p>Effect of C.I. Acid Black 1 on chlorophyll <it>a </it>content of <it>L. valderiana </it>BDU20041 in ASN III nitrogen free medium</p></caption><text>
   <p><b>Effect of C.I. Acid Black 1 on chlorophyll <it>a </it>content of <it>L. valderiana </it>BDU20041 in ASN III nitrogen free medium</b>.</p>
</text><graphic file="1746-1448-6-6-2" hint_layout="single"/></fig>
<fig id="F3"><title><p>Figure 3</p></title><caption><p>Effect of C.I. Acid Black 1 on phycobilins content of <it>L. valderiana </it>BDU20041 in ASN III nitrogen free medium at the end of 12 days</p></caption><text>
   <p><b>Effect of C.I. Acid Black 1 on phycobilins content of <it>L. valderiana </it>BDU20041 in ASN III nitrogen free medium at the end of 12 days</b>.</p>
</text><graphic file="1746-1448-6-6-3" hint_layout="single"/></fig>
<p>The second notable feature is the total ROS produced in stress response which is represented as 2', 7'- Dichorofluorescein (DCF) with relative fluorescence intensity at 520 <it>nm</it>. Generally, ROS levels increase in response to abiotic stress <abbrgrp>
<abbr bid="B20">20</abbr>
</abbrgrp>. Decreased levels of ROS initially in the 3<sup>rd </sup>h with <it>L. valderiana </it>BDU20041 dosed with dye may be due to its involvement in degradation whereas, within 24 h, the organism increases the rate of ROS production and showed sustenance (Figure <figr fid="F4">4</figr>).</p>
<fig id="F4"><title><p>Figure 4</p></title><caption><p>Time course measurement of DCF oxidation (<it>invivo </it>ROS) by <it>L. valderiana </it>BDU20041 treated and untreated with C.I. Acid Black 1 (100 mG L<sup>-1</sup>)</p></caption><text>
   <p><b>Time course measurement of DCF oxidation (<it>invivo </it>ROS) by <it>L. valderiana </it>BDU20041 treated and untreated with C.I. Acid Black 1 (100 mG L<sup>-1</sup>)</b>.</p>
</text><graphic file="1746-1448-6-6-4" hint_layout="double"/></fig>
<p>The initial decrease in total ROS in dye dosed culture could be attributed to two reasons (i) role of ROS in dye decolourization <abbrgrp>
<abbr bid="B21">21</abbr>
<abbr bid="B22">22</abbr>
<abbr bid="B23">23</abbr>
</abbrgrp> (ii) the free radical generated passes through the Asada-Halliwell pathway initiated by SOD that converts the highly reactive oxy-radicals through an array of reaction to less toxic forms <abbrgrp>
<abbr bid="B19">19</abbr>
<abbr bid="B24">24</abbr>
</abbrgrp>. Further, the sustenance of ROS clearly depicts the stress response in <it>L. valderiana </it>BDU20041 as cyanobacteria maintain their antioxidants level by release of reactive oxygen species into the <it>milieu </it>
<abbrgrp>
<abbr bid="B5">5</abbr>
<abbr bid="B24">24</abbr>
</abbrgrp>. Studies with eukaryotic and bacterial systems showed that, low levels of AOS are indispensable to act in cellular signaling and in the control of gene expression <abbrgrp>
<abbr bid="B25">25</abbr>
</abbrgrp>. Because of the dual functions of ROS, a tight control of their concentrations may be anticipated, which requires a delicate balance of systems involved in their generation and destruction <abbrgrp>
<abbr bid="B26">26</abbr>
</abbrgrp>.</p>
<p>Hence, the third significant trait studied was the response of SOD enzyme to oxidative stress (in this case, C.I. Acid Black 1). SOD activity was found to increase in the 3<sup>rd </sup>h and on further exposure to dye, the activity increased two-fold and got sustained thereafter (Figure <figr fid="F5">5</figr>). This obviously proves that SOD plays a significant role in alleviating oxidative stress in <it>L. valderiana </it>BDU20041.</p>
<fig id="F5"><title><p>Figure 5</p></title><caption><p>Time course measurement on effect of C.I. Acid Black 1 on superoxide dismutase activity of <it>L. valderiana </it>BDU20041 in ASN III nitrogen free medium</p></caption><text>
   <p><b>Time course measurement on effect of C.I. Acid Black 1 on superoxide dismutase activity of <it>L. valderiana </it>BDU20041 in ASN III nitrogen free medium</b>.</p>
</text><graphic file="1746-1448-6-6-5" hint_layout="double"/></fig>
<p>As the initial oxy-radical product to be formed under any oxidative stress is the superoxide radical (O<sub>2</sub>
<sup>-.</sup>) which upon further reaction within the cell can generate more ROS such as hydroxyl radicals and singlet oxygen. Superoxide dismutases are metalloenzymes that dismutase these superoxide radical to hydrogen peroxides. Their activity increases on exposure to oxidative stress <abbrgrp>
<abbr bid="B16">16</abbr>
</abbrgrp>. Hence, they can be depicted as the central dogma of antioxidative system. Hence, in our study attempts was made to isolate and characterize the SOD gene involved in abating oxidative stress caused by C.I. Acid Black 1.</p>
<p>The SOD gene from the DNA isolated of marine cyanobacterium, <it>L. valderiana </it>BDU20041 was amplified using the below mentioned primers. Electrophoresis of the amplified products of gradient PCR (61&#176;C) showed a band of 550 <it>bp </it>and none in negative control (Figure <figr fid="F6">6</figr>). The nucleotide sequence of the partial SOD gene of 432 <it>bp </it>was submitted to GenBank database (<ext-link ext-link-id="AY974247" ext-link-type="gen">AY974247</ext-link>) and their deduced aminoacid was 144 residues (<ext-link ext-link-id="AAX84682" ext-link-type="gen">AAX84682</ext-link>) (Figure <figr fid="F7">7</figr>). The computational analysis on the sequenced partial SOD gene comprised of an N-terminal and a C-terminal region from 1 to 63 and 70 to 143 residues respectively with a theoretical molecular weight of 15.5 <it>KDa</it>.</p>
<fig id="F6"><title><p>Figure 6</p></title><caption><p>Agarose gel electrophorogram (1.5%) showing an amplified MnSOD product of 550 bp from <it>Leptolyngbya valderiana </it>BDU20041</p></caption><text>
   <p><b>Agarose gel electrophorogram (1.5%) showing an amplified MnSOD product of 550 bp from <it>Leptolyngbya valderiana </it>BDU20041</b>. Lane1- 1 Kb marker, Lane 2- Negative control, Lane 3- Amplified PCR product.</p>
</text><graphic file="1746-1448-6-6-6" hint_layout="double"/></fig>
<fig id="F7"><title><p>Figure 7</p></title><caption><p>Nucleotide Sequence for MnSOD of <it>Leptolyngbya valderiana </it>BDU20041</p></caption><text>
   <p><b>Nucleotide Sequence for MnSOD of <it>Leptolyngbya valderiana </it>BDU20041</b>. Shown below nucleotide (<ext-link ext-link-id="AY974247" ext-link-type="gen">AY974247</ext-link>) is the translated protein (<ext-link ext-link-id="AAX84682" ext-link-type="gen">AAX84682</ext-link>) sequence used for structure determination.</p>
</text><graphic file="1746-1448-6-6-7" hint_layout="double"/></fig>
<p>When the obtained sequence was aligned within cyanobacterial SOD, MnSOD of <it>Thermosynechococcus elongates </it>BP1 (<ext-link ext-link-id="BAC07589" ext-link-type="gen">BAC07589</ext-link>) and <it>Leptolyngbya boryana </it>(<ext-link ext-link-id="P50058" ext-link-type="gen">P50058</ext-link>) had maximum homology of 47%. The least homology of 43% was shared with <it>Leptolyngbya boryana </it>(<ext-link ext-link-id="P50056" ext-link-type="gen">P50056</ext-link>). The homology difference could be attributable to partial SOD gene, in particular C-terminal region where most of the aminoacids are highly conserved residues along with motif region (DVWEHAYY).</p>
<p>Further, the isolated sequence on analysis (Figure <figr fid="F8">8</figr>) showed the presence of first 3 residues of SOD motif region DVWEHAYY (D<sub>281</sub>-W<sub>223</sub>) along with conserved residues-glycine (G<sub>53</sub>), histidine (H<sub>55</sub>), phenylalanine (F<sub>61</sub>), serine (S<sub>105</sub>), tryptophan (W<sub>108</sub>), leucine (L<sub>109</sub>), arginine (N<sub>125</sub>) and glutamine (Q<sub>126</sub>). These highly conserved residues were found to be precise for cyanobacterial MnSOD as described by Priya et al <abbrgrp>
<abbr bid="B7">7</abbr>
</abbrgrp>.</p>
<fig id="F8"><title><p>Figure 8</p></title><caption><p>Sequence alignment of cyanobacterial Manganese superoxide dismutase</p></caption><text>
   <p><b>Sequence alignment of cyanobacterial Manganese superoxide dismutase</b>. Alignment showing 95% conserved residues using Clustal W of BioEdit Package (v.7.0.5) <abbrgrp><abbr bid="B33">33</abbr></abbrgrp> Residues involved in active site are highlighted in red, metal specific residues in pink and highly conserved residues for MnSOD in green.</p>
</text><graphic file="1746-1448-6-6-8" hint_layout="double"/></fig>
<p>All living systems have only one of each type of SOD in the various cellular compartments indicating that they have far more complex antioxidant defenses than other organisms. As per the findings of Parker and Blake <abbrgrp>
<abbr bid="B27">27</abbr>
</abbrgrp>, Jackson and Copper <abbrgrp>
<abbr bid="B28">28</abbr>
</abbrgrp> and Priya et al <abbrgrp>
<abbr bid="B7">7</abbr>
</abbrgrp> our analysis of gene sequence of <it>L. valderiana </it>BDU20041 shows that the residues histidine (H<sub>4</sub>, H<sub>58</sub>) and aspartate (D<sub>141</sub>) plays a role in active sites (Figure <figr fid="F8">8</figr>, <figr fid="F9">9</figr>). In addition, the presence of important metal specific residues <it>viz</it>., glycine (G<sub>54</sub>), isoleucine (I<sub>81</sub>), glycine (G<sub>106</sub>), tryptophan (W<sub>107</sub>) and proline (P<sub>129</sub>) concludes that the metalloform isolated from <it>L. valderiana </it>BDU20041 is that of Mn (Figure <figr fid="F8">8</figr>, <figr fid="F9">9</figr>).</p>
<fig id="F9"><title><p>Figure 9</p></title><caption><p>Metal binding sites of predicted MnSOD of <it>L. valderian</it>a BDU20041</p></caption><text>
   <p><b>Metal binding sites of predicted MnSOD of <it>L. valderian</it>a BDU20041</b>. Catalytically essential aspartate or histidine residues are represented in ball and stick mode. Structures are visualized using WebLab ViewerLite 4.2 software <abbrgrp><abbr bid="B36">36</abbr></abbrgrp>.</p>
</text><graphic file="1746-1448-6-6-9" hint_layout="double"/></fig>
<p>The elucidated structure possesses 6 helices and 3 sheets (Figure <figr fid="F10">10</figr>). Homology modeling with MnSOD of <it>L. valderiana </it>BDU 20041 showed a similarity of 63.76% with <it>Bacillus anthracis </it>(<ext-link ext-link-id="1XUQ" ext-link-type="pdb">1XUQ</ext-link>) and 60.98% with <it>Deinococcus radiodurans </it>(<ext-link ext-link-id="1Y67" ext-link-type="pdb">1Y67</ext-link>) (Figure <figr fid="F11">11</figr>). The RMSD value of superposed structure shows that the alpha carbons are at 0.88A and backbone carbon is at 0.85. This further substantiates that the isolated SOD gene is MnSOD with its co-coordinating residues at position His<sub>4</sub>, His<sub>58 </sub>and Asp<sub>141 </sub>(Figure <figr fid="F9">9</figr>).</p>
<fig id="F10"><title><p>Figure 10</p></title><caption><p>Predicted structure of MnSOD of <it>L. valderian</it>a BDU20041</p></caption><text>
   <p><b>Predicted structure of MnSOD of <it>L. valderian</it>a BDU20041</b>. Monomeric subunit of MnSOD represents helix (red) and strands (blue). Structures are visualized using WebLab ViewerLite 4.2 software <abbrgrp><abbr bid="B36">36</abbr></abbrgrp>.</p>
</text><graphic file="1746-1448-6-6-10" hint_layout="double"/></fig>
<fig id="F11"><title><p>Figure 11</p></title><caption><p>Superposed structure of MnSOD of <it>L. valderiana </it>BDU20041</p></caption><text>
   <p><b>Superposed structure of MnSOD of <it>L. valderiana </it>BDU20041</b>. Monomeric subunit of MnSOD of <it>Bacillus anthracis </it>(<ext-link ext-link-id="1XuQB" ext-link-type="pdb">1XuQB</ext-link>) depicted red with <it>L. valderiana </it>BDU20041 (AAX84682) in yellow sharing 63.8% homology.</p>
</text><graphic file="1746-1448-6-6-11" hint_layout="double"/></fig>
<p>The radial neighbor-joining (NJ) analysis of all cyanobacterial SODs from public database (NCBI/DDBJ/EMBL) showed four distinct metalloforms <it>viz</it>., Mn, Fe, Cu/Zn and NiSODs. The SOD gene from <it>L. valderiana </it>BDU 20041 is found to be grouped with MnSODs (Figure <figr fid="F12">12</figr>).</p>
<fig id="F12"><title><p>Figure 12</p></title><caption><p>Phylogenetic tree (radial) of cyanobacterial superoxide dismutases using Neighbour-Joining method using Phylodraw (v.0.8) <abbrgrp><abbr bid="B37">37</abbr></abbrgrp></p></caption><text>
   <p><b>Phylogenetic tree (radial) of cyanobacterial superoxide dismutases using Neighbour-Joining method using Phylodraw (v.0.8) </b><abbrgrp><abbr bid="B37">37</abbr></abbrgrp>.</p>
</text><graphic file="1746-1448-6-6-12" hint_layout="double"/></fig>
<p>The identified MnSOD indicates that it is one of the most probable means through which marine cyanobacterium, <it>L. valderiana </it>BDU20041 alleviates oxidative stress caused by abiotic factors (C.I. Acid Black 1).</p>
</sec>
<sec>
<st>
<p>Materials and methods</p>
</st>
<sec>
<st>
<p>Azo Dye</p>
</st>
<p>The diazo dye, Acid Black 1 (C.I. 20470, Aldrich) was used in the study. Stock solution was prepared by dissolving dye in deionized water and sterilized by membrane filtration (0.2 &#956;M) Millipore.</p>
</sec>
<sec>
<st>
<p>Cyanobacterial strain</p>
</st>
<p>Axenic culture of <it>Leptolyngbya valderiana </it>BDU20041 from the germplasm of National Facility for Marine Cyanobacteria (NFMC), Tiruchrappalli, Tamil Nadu, was utilized in this study. The cells were grown photoautotrophically under continuous illumination with white fluorescent light at about 200 &#956;mol photon m<sup>-2 </sup>s<sup>-1 </sup>in 250 mL Erlenmeyer flasks containing artificial sea water (ASN III) medium <abbrgrp>
<abbr bid="B29">29</abbr>
</abbrgrp> at 25 &#177; 2&#176;C for a week.</p>
</sec>
<sec>
<st>
<p>Experimental conditions</p>
</st>
<p>The medium ASN III <abbrgrp>
<abbr bid="B29">29</abbr>
</abbrgrp> was modified as either ASN III nitrogen free medium (without NaNO<sub>3</sub>) or nitrogen limited medium (with a low concentration of 5 mG L<sup>-1 </sup>NaNO<sub>3</sub>). The organism was grown in ASN III medium for 5 days initially and then in ASN III N limited medium for 5 days at 27 &#177; 2&#176;C at 20 &#956;mol photon m<sup>2 </sup>s<sup>-1 </sup>light intensity, unless otherwise stated. Mid-log cultures were centrifuged; the harvested cells were washed with nitrogen free medium and resuspended in the same medium. This was used as inoculum for all the experiments; the results are presented as means of triplicates.</p>
</sec>
<sec>
<st>
<p>Decolourization assay</p>
</st>
<p>The decolourization studies were performed by inoculating an equal volume of cultures (500 &#956;L, based on chlorophyll content) to test tubes with 4.5 mL nitrogen free ASNIII medium containing filter sterilized dye, C.I. Acid Black 1 to a final concentration of 0.01%. The cultures were incubated for a stipulated period of 12 days in the above said conditions. Respective abiotic (medium with 0.01% dye only) and biotic (medium with organism only) controls were also maintained in similar conditions as mentioned above.</p>
<p>Culture was harvested by centrifugation at 5,000 g for 10 min on day 0, 1, 2, 6 and 12. The absorption spectrum of the clear supernatant from 400 to 700 <it>nm </it>was recorded using a spectrophotometer (JASCO V-550 UV-Visible spectrophotometer, Japan). The percentage of decolourization was calculated as follows</p>
<p>
<display-formula>
<graphic file="1746-1448-6-6-i1.gif"/>
</display-formula>
</p>
<p>where, A = initial absorbance at zero hour, B = final absorbance.</p>
</sec>
<sec>
<st>
<p>Preparation of enzyme extract</p>
</st>
<p>Cyanobacterial culture was pelleted by centrifugation at 10,000 &#215; g for 10 min and was washed with ice-cold 25 mM Tris-Cl, pH7.0 and homogenized with the same buffer using Braun sonicator (Labsonic 2000 UB), Germany on an ice bath. Crude lysate was clarified several times by centrifugation at 15,000 <it>g </it>for 15 min at 4&#176;C. The clear supernatant obtained served as crude intracellular enzyme source.</p>
</sec>
<sec>
<st>
<p>SOD assay</p>
</st>
<p>SOD activity was assayed by measuring its ability to inhibit the photochemical reduction of nitroblue tetrazolium (NBT) using the method of Beauchamp and Fridovich <abbrgrp>
<abbr bid="B30">30</abbr>
</abbrgrp>.</p>
</sec>
<sec>
<st>
<p>In vivo detection of ROS using DCFH-DA</p>
</st>
<p>The production of Reactive Oxygen Species (ROS) that includes both active oxygen and nitrogen species was detected by using 2',7'-Dichlorofluorescein diacetate (DCFH-DA) in dye (C.I Acid Black 1, 100 mG L<sup>-1</sup>) treated cultures at 3, 24 and 48 hr following He and Hader <abbrgrp>
<abbr bid="B14">14</abbr>
</abbrgrp>. DCFH-DA cannot be added or incubated prior to dye treatment due to rapid autooxidation of DCFH-DA or hydrolysed 2, 7-dichlorodihydrofluorescein (DCFH) by exposure to light <abbrgrp>
<abbr bid="B15">15</abbr>
</abbrgrp>. Therefore, DCFH-DA (final concentration 5 &#956;M from stock solution of 2 mM) was immediately added to the dye treated and incubated on a shaker at room temperature in dark at 27 &#177; 2&#176;C for 1 h. The fluorescence of the samples was measured with a spectroflurometer (JASCO V550 spectroflurometer, Japan) at room temperature, with excitation wavelength of 485 <it>nm </it>and emission wavelengths at 520 <it>nm </it>to determine the relative ROS production. The results were corrected by subtracting the fluorescence of dye untreated control samples.</p>
</sec>
<sec>
<st>
<p>DNA isolation</p>
</st>
<p>For genomic DNA isolation, actively growing cells were harvested by centrifugation (10,000 &#215; g, 5 min), washed twice with sterile double distilled water followed by a final wash with TE buffer (10 mM Tris: 1 mM EDTA, pH 8.0). Total genomic DNA was extracted using the xanthogenate nucleic acid isolation protocol described by Tillet and Neilan <abbrgrp>
<abbr bid="B31">31</abbr>
</abbrgrp>.</p>
</sec>
<sec>
<st>
<p>PCR amplification and cloning of amplified gene</p>
</st>
<p>Oligonucleotide primers corresponding to two separate conserved regions were designed based on the published nucleotide sequence of cyanobacterial Fe/MnSOD and used for PCR amplification of DNA fragment coding for partial SOD gene. The sequence of the primers were 5'-CAC C(C/A)T TGC C(C/T)T A(C/T)G-3' and 5'-GAG GTA GTA AGC (G/A)TG TTC CCA-3'. The PCR reaction was performed using Mastermix (Eppendorf, Germany) containing 1 U <it>Taq </it>DNA polymerase, 0.10 &#956;M of each primer, and 50 nG of template DNA in a 25.0 &#956;L reaction mixture using a Master gradient thermal cycler (Eppendorf, Germany). The cycling profile included an initial denaturation at 94&#176;C for 3 minutes followed by 29 cycles of 94&#176;C for 1 min, 53&#176;C for 1 min (gradient, G = 10&#176;C), 72&#176;C for 1 min, and a final extension at 72&#176;C for 6 minutes. Sterile water replaced DNA for the control. Five microliters of the amplified products were subjected to 1.5% agarose gel electrophoresis containing ethidium bromide (2.25 mg ml<sup>-1 </sup>distilled water) in 1&#215; TAE (40 mM Tris-acetate: 1 mM EDTA), visualized with a UV transilluminator and documented using CCD camera (Alpha Imager&#8482; 2200, USA).</p>
<p>The resulting amplicons was purified with the Qiagen gel extraction kit (Qiagen GmbH, Hilden, Germany) and subcloned into the pGEM-T vector (Promega, Madison, WI) following the directions of the manufacturer. The construct was transformed into DH5&#945; competent cells using electroporation with 1800V, 25 microfarads, and 200 <it>ohms </it>in a Gene Pulser II electroporation system (Bio-Rad).</p>
</sec>
<sec>
<st>
<p>DNA sequencing</p>
</st>
<p>Clones were sequenced using M13 forward and reverse oligonucleotide primers (Integrated DNA Technologies, USA) for the DNA cycle sequencing reaction kit following recommended protocol. The DNA sequences of the amplified product were obtained with an ABI 310 automated sequencer using the chain-termination method with big-dye terminators (Applied Biosystems, Foster, CA, USA). For the sequence data, automated base calls were checked by manual inspection of the electropherograms of both forward and reverse sequences. The base call conflicts were resolved by aligning and comparing both strands using SeqScape<sup>&#174; </sup>software v 2.5 (Applied Biosystems, Foster, CA, USA).</p>
</sec>
<sec>
<st>
<p>Characterization of isolated SOD gene</p>
</st>
<p>The computational analysis of the isolated gene was carried out using protein analysis <abbrgrp>
<abbr bid="B32">32</abbr>
</abbrgrp>, sequence alignment (Clustal W) of BioEdit <abbrgrp>
<abbr bid="B33">33</abbr>
</abbrgrp>, domain pattern <abbrgrp>
<abbr bid="B34">34</abbr>
</abbrgrp>, homology modeling and analysis <abbrgrp>
<abbr bid="B35">35</abbr>
</abbrgrp> and visualized using WebLab ViewerLite <abbrgrp>
<abbr bid="B36">36</abbr>
</abbrgrp>. Phylogenetic tree was constructed using multiple alignments and visualized in Phylodraw v.0.8 <abbrgrp>
<abbr bid="B37">37</abbr>
</abbrgrp>.</p>
</sec>
<sec>
<st>
<p>Nucleotide Sequence Accession Numbers</p>
</st>
<p>The nucleotide sequence of the SOD gene has been deposited in NCBI under accession no. <ext-link ext-link-id="AY974247" ext-link-type="gen">AY974247</ext-link>.</p>
</sec>
</sec>
<sec>
<st>
<p>Competing interests</p>
</st>
<p>The authors declare that they have no competing interests.</p>
</sec>
<sec>
<st>
<p>Authors' contributions</p>
</st>
<p>BP and KRS carried out the molecular genetic studies, participated in the sequence alignment and drafted the manuscript. VDJ helped in carrying out the structural comparison. GS helped in fine tuning of the manuscript. LU and DP conceived of the study and participated in its design and coordination. All authors read and approved the final manuscript.</p>
</sec>
</bdy><bm>
<ack>
<sec>
<st>
<p>Acknowledgements</p>
</st>
<p>This study was supported by the grant from Department of Biotechnology, Government of India, New Delhi. The authors thank Mr. Jagadeesan Premanandh (Part-Time Research Scholar) for his valuable suggestions.</p>
</sec>
</ack>
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