<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">GEP</journal-id><journal-title-group><journal-title>Journal of Geoscience and Environment Protection</journal-title></journal-title-group><issn pub-type="epub">2327-4336</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/gep.2017.59010</article-id><article-id pub-id-type="publisher-id">GEP-78973</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Earth&amp;Environmental Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  UV-A Activated ZnO Mediated Photocatalytic Decolorization of Nigrosine (Acid Black 2) Dye in Aqueous Solution
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Mohammed</surname><given-names>Thamer Jaafar</given-names></name><xref ref-type="aff" rid="aff1"><sub>1</sub></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib></contrib-group><aff id="aff1"><label>1</label><addr-line>Department of Petroleum &amp;amp; Petrochemical Engineering, College of Engineering, Kerbala University, Kerbala, Iraq</addr-line></aff><author-notes><corresp id="cor1">* E-mail:<email>dr.mohammedthamer@yahoo.com</email></corresp></author-notes><pub-date pub-type="epub"><day>22</day><month>08</month><year>2017</year></pub-date><volume>05</volume><issue>09</issue><fpage>138</fpage><lpage>147</lpage><history><date date-type="received"><day>1,</day>	<month>August</month>	<year>2017</year></date><date date-type="rev-recd"><day>8,</day>	<month>September</month>	<year>2017</year>	</date><date date-type="accepted"><day>11,</day>	<month>September</month>	<year>2017</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p><html>
 <head></head>
 
  The present study deals with studied the essential requirements for photo-decoulorization of nigrosine dye with suspension solution of photocatalyst (ZnO), under 250 Watt UV-A light (
  <em>I<sub>o</sub></em> = 1.47 
  <img src="Edit_620acfe4-9504-42c1-ba89-d7a3d6bd4652.bmp" alt="" />10
  <sup>-7</sup> ensien s
  <sup>-1</sup>). A kinetics study of photo-decolourization for this dye was obeyed to pseudo-first order. The best initial pH of decolorization at 25 mg/L of dye solution with 300 mg of ZnO was given a fast reaction at 8.17. The calculated activation energy for this photoreaction was found to be 31.549 kJ
  &#183;mol
  <sup>-1</sup>. Thermodynamically, the reaction is exothermic and spontaneously. The efficiency of decolorizatio E% was 97.077 at 15 min that decreased with addition oxidant reagents such as H
  <sub>2</sub>O
  <sub>2</sub>, Fe
  <sup>2+</sup> and mixture from them.
 
</html></p></abstract><kwd-group><kwd>Nigreson Dye</kwd><kwd> Acid Black 2 Dye</kwd><kwd> Photocatalytic</kwd><kwd> Decolorization</kwd><kwd> Oxidant Reagents</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>There are more than 100,000 varieties of dyes available in the market, which used in the textile, cosmetics, food, paper, leather industries and Medications industries. Whereas over 700,000 tons per were produced in worldwide. About 10% of the above amount of used dye is lost as wastewater, which affected on the environment by leading to Poisoning of living organisms [<xref ref-type="bibr" rid="scirp.78973-ref1">1</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref2">2</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref3">3</xref>] .</p><p>During the Industrial Revolution, the synthetic dyes were quickly replaced with the commercial textiles manufactured and unlike the natural dyes, because of these dyes were suitable for synthetic fibers [<xref ref-type="bibr" rid="scirp.78973-ref4">4</xref>] .</p><p>Nigrosin dye is a mixture of artificial black dyes (CI 50415, Solvent black 5) made by heating a mixture of aniline, nitrobenzene and aniline hydrochloride in found the existence of catalyst like copper or iron. The advantage of sulfonation of nigrosine dye is yielded it ability for solubling in water as anionic dye. The main industrial employed for nigrosin dye is done as a marker-pen inks and colorant for varnishes. In biology field, the nigrosin dye is employed for negative Staining bacteria, as well as the capsule-containing fungus and Cryptococcus neoformans [<xref ref-type="bibr" rid="scirp.78973-ref5">5</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref6">6</xref>] .</p><p>Heterogeneous photocatalysis has performed an adevastating mission technology that caused to the total mineralization of most of the organic pollutants like organic dyes. Titania (TiO<sub>2</sub>) is the most commonly employed effective photocatalyst for a wide range of organic chemical degradation. In recent years, ZnO is another important semiconductor investigated. In some cases, ZnO, has been more effective than TiO<sub>2</sub>. ZnO is regarded as a representative of the metal oxide class, which is played an important role to the study of electrochemistry and catalysis. The ZnO nanoparticle has received much attention because it has a low cost of production, responded to UV light to have a band gap range 3.2 - 3.3 eV, and high photoactivity in several photochemical and photoelectron-chemical processes. All these characteristic of it that lead to use it in eliminating environmental pollution [<xref ref-type="bibr" rid="scirp.78973-ref7">7</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref8">8</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref9">9</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref10">10</xref>] .</p><p>The aim of this work was focused on the studied of the effect of initial pH , temperatures and oxidation reagent on photodecolorization of Nigresoine dye in suspension solution of ZnO.</p></sec><sec id="s2"><title>2. Materials and Method</title><p>All used chemicals in this work were employed without further purification. 99.5% purity of commercial ZnO was supplied by Fluka. Nigrosin dye has molecular weight equal to 616.49 g・mol<sup>−1</sup>, IUPAC name is mono (4,4’-((5-phenyl-9- (phenylamino) phenazine-5-ium-2,3 diyl) bis(azanediyl)) dibenzenesulfonate), synonym is Acid Black 2, molecular formula (C<sub>22</sub>H<sub>14</sub>N<sub>6</sub>Na<sub>2</sub>O<sub>9</sub>S<sub>2</sub>), the chemical family beyonds to Aniline derivatives, classification as acid dye and supplied by High Purity Laboratory Chemicals (HPLC), Mumbai. The chemical structure for Nigrosin dye is illustrated in (<xref ref-type="fig" rid="fig1">Figure 1</xref>).</p><p><xref ref-type="fig" rid="fig1">Figure 1</xref>. The chemical structure for Nigrosin dye.</p><p>The photocatalytic decolorization by using ZnO experiments were done by employing home made photoreactor that consists of 250 Watt high pressure mercury lamp at light intensity I<sub>o</sub> equal to 1.47 &#215; 10<sup>−7</sup> ensien s<sup>−1</sup> that calculated by chemical actinometer (ferrioxalate actinometric) [<xref ref-type="bibr" rid="scirp.78973-ref11">11</xref>] , magnetic stirrer, wooden box that used to prevent the escape of harmful radiation [<xref ref-type="bibr" rid="scirp.78973-ref12">12</xref>] , fan, Pyrex glass beaker and Teflon bar.</p><p>25 ppm of Nigrosin dye was mixed with 300 mg of ZnO to generate a suspension solution by employing a magnetic stirrer. The mixing process was continued without irradiation in dark reaction for 30 min, and then the mixture was activated via the light irradiation in photocatalytic process. About 3 mL of suspention solution was collected at 5 min as a sequence time by using a plastic test tube. The withdrawn suspention was centrifuged at 4000 rpm for 10 minutes and filtered. The centrifuged process was repeated to ensure the completed of removing the catalyst before found the residual concentration of dye . To find the residual concentration of Nigrosin dye was measured using spectrophotometry at 570 nm.</p><p>The rate constant for this reaction was determined by depending upon the Langmuir-Hinshelwood (L-H) model that modified to investigate the order of the studied photoreaction, from the following equations [<xref ref-type="bibr" rid="scirp.78973-ref13">13</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref14">14</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref15">15</xref>] :</p><p>C t = C o exp ( − k a p p ⋅ t ) (1)</p><p>where: C<sub>o</sub> is an initial concentration of Nigrosin dye in (dark reaction) at time of irradiation = 0, C<sub>t</sub> is a concentration of the same dye at time t of irradiation.</p><p>ln C o C t = k a p p ⋅ t (2)</p><p>Equation (2) was applied, at assumption the initial concentration of dye is low, hence, the rate of photo reaction follows pseudo first-order kinetics [<xref ref-type="bibr" rid="scirp.78973-ref14">14</xref>] . The effeciency of decolorization E% was assessed [<xref ref-type="bibr" rid="scirp.78973-ref14">14</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref16">16</xref>] in Equation (3).</p><p>E % = C o − C t C o &#215; 100 (3)</p></sec><sec id="s3"><title>3. Results and Discussion</title><sec id="s3_1"><title>3.1. Effect of pH</title><p>The initial pH is regarded as a vital parameter to study the photoreaction for decolorization any dye from suspension solution of photocatalyst. The effect of pH from 4 to 10 on the photocatalytic decolorization of Nigrosin dye are appeared in (<xref ref-type="fig" rid="fig2">Figure 2</xref>(a) and <xref ref-type="fig" rid="fig2">Figure 2</xref>(b)) and <xref ref-type="fig" rid="fig3">Figure 3</xref>.</p><p>The results demonstrated that the best initial pH for decolorization of Nigrosin dye is 8.177. This value is near from the zero point charge of ZnO that equal to 9 [<xref ref-type="bibr" rid="scirp.78973-ref12">12</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref17">17</xref>] . This effect depended upon the characteristics of studied dye, the surface charge of catalyst and generation of hydroxyl radicals via photocatalysis process [<xref ref-type="bibr" rid="scirp.78973-ref18">18</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref19">19</xref>] . In acid medium, the surface of photocatalyst is positive chargly and caused photocorrosion via self oxidation, therebye the efficiency of</p><p>decolorization depresses. Moreover, In basic medium, the surface of photocatalyst is negative charge, that will lead to dissolution of the photocatalyst according to the following Equations (4)-(7) [<xref ref-type="bibr" rid="scirp.78973-ref19">19</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref20">20</xref>] .</p><p>ZnO + 2 h + → Z n 2 + + 1 2 O 2                           ( a c i d i c   p H ) (4)</p><p>o r           ZnO + 2 H + → Z n 2 + + H 2 O                       ( a c i d i c   p H ) (5)</p><p>Z n − OH + O H − → Z n − O − + H 2 O                     ( b a s i c   p H ) (6)</p><p>o r       ZnO + H 2 O + 2 O H − → [ Z n ( O H ) 4 ] 2 −                 ( b a s i c   p H ) (7)</p><p><xref ref-type="fig" rid="fig3">Figure 3</xref> was proved, at initial pH equal to 8.170, the maximum value of the efficiency (E%) of removal Nigrosin dye in presence of ZnO is reached to 99.014 at 25 min and 288.15 K.</p></sec><sec id="s3_2"><title>3.2. Effect of Temperature</title><p>The effect of temperature on photodecolorization of Nigresone dye from suspension solution of ZnO was estimated in the range (283.15 - 303.15) K. This effect plays an important role to determine the apparent activation energy (E<sub>a</sub>) that used Arrhenius equation (Equation (8)), and some thermodynamics parameters such as (ΔH<sup>#</sup>, ΔS<sup>#</sup> and ΔG<sup>#</sup>) that employed Eyring-Polanyi equation (Equation (9)) and Gibbs equation (Equation (10)). These parameters were calculated by the following Equations [<xref ref-type="bibr" rid="scirp.78973-ref21">21</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref22">22</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref23">23</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref24">24</xref>] .</p><p>ln k a p p = − E a R T + ln A (8)</p><p>Whereas: k<sub>app</sub> is apparent rate constant, E<sub>a</sub> is apparent activation energy, A is a frequency constant, R is gas constant and T is temperature of photoreaction.</p><p>ln ( k a p p T ) = − Δ H # R T + ( ln k B h + Δ S # R ) (9)</p><p>Whereas: k<sub>B</sub> is a Boltzmann’s constant, h is a Plank’s constant, R is a gas</p><p>constant and T is the temperature of reaction.</p><p>Δ G # = Δ H # − T Δ S # (10)</p><p>From (<xref ref-type="fig" rid="fig4">Figure 4</xref>(a) and <xref ref-type="fig" rid="fig4">Figure 4</xref>(b)), it was observed the decolorization of the studied dye declines with increasing temperature that due to the exothermic nature in reaction (ΔH<sup>#</sup>). This result is in agreement with information that reported in references [<xref ref-type="bibr" rid="scirp.78973-ref21">21</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref25">25</xref>] .</p><p>On basis on calculated data from <xref ref-type="fig" rid="fig4">Figure 4</xref>(a) and <xref ref-type="fig" rid="fig4">Figure 4</xref>(b), the values of activation energy and the essential thermodynamics parameters that are listed in <xref ref-type="table" rid="table1">Table 1</xref>.</p><p>The negative value of ΔG<sup>#</sup> for this photoreaction indicates the reaction spontaneous in nature. The negative value of ΔS<sup>#</sup> proved the depress randomness.</p><table-wrap id="table1" ><label><xref ref-type="table" rid="table1">Table 1</xref></label><caption><title> The activation kinetic and thermodynamic parameters that calculated for photodecolorisation of Nigresine dye with suspension solution of ZnO</title></caption><table><tbody><thead><tr><th align="center" valign="middle" >E<sub>a</sub> kJ・mol<sup>−1</sup></th><th align="center" valign="middle" >ΔH<sup>#</sup> kJ・mol<sup>−1</sup></th><th align="center" valign="middle" >ΔS<sup>#</sup> kJ・mol<sup>−1</sup>・K<sup>−1 </sup></th><th align="center" valign="middle" >ΔG<sup>#</sup><sub>303.15</sub> kJ・mol<sup>−1</sup></th></tr></thead><tr><td align="center" valign="middle" >30.71025</td><td align="center" valign="middle" >−33.1479</td><td align="center" valign="middle" >−0.00546</td><td align="center" valign="middle" >−31.4927</td></tr></tbody></table></table-wrap><p>The moderate value of activation energy refer to the rate for decolorization of this dye is low and reach to final at 25 min.</p></sec><sec id="s3_3"><title>3.3. Effect of Addition Oxidant Reagents</title><p><xref ref-type="fig" rid="fig5">Figure 5</xref> displays the effect of addition of varies types of oxidant reagent such as H<sub>2</sub>O<sub>2</sub> and Fe(II) on the decolorization of Nigrosein dye in suspension solutuion of ZnO.</p><p>In case of used ZnO alone as photocatalyst, The E% for decolorization of above-mentioned dye is equal to 64.9122 at 30˚C (Lab temperature) and<sup> </sup>15 min. The hydroxyl radical acts as a power for starting the photoreaction with presence of photocatalyst. This progress of photoreaction was monitored by the following equations [<xref ref-type="bibr" rid="scirp.78973-ref26">26</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref27">27</xref>] .</p><p>ZnO + h v → ZnO ( e CB − + h VB + ) (11)</p><p>H 2 O + h VB + → H + + HO &#183; (12)</p><p>O 2 + e CB − → O 2 &#183; − (13)</p><p>O 2 &#183; − + H + → HO 2 . (14)</p><p>HO 2 &#183; + H + → H 2 O 2 (15)</p><p>H 2 O 2 + h v → 2 HO &#183; (16)</p><p>The decolorization of Nigresine dye will suggest in the following equation</p><p>Dye + HO &#183; → n CO 2 + n H 2 O + Inorganicions ( NH 4 + , SO 4 2 − + Na + ) (17)</p><p>When addition 1% of H<sub>2</sub>O<sub>2</sub> to suspension solution of dye and ZnO, that depress the E% to 58.969, that attributable to the high concentration of H<sub>2</sub>O<sub>2</sub> that acts as scavenger for •OH radical to form Perhydroxyl radical HO 2 &#183; [<xref ref-type="bibr" rid="scirp.78973-ref12">12</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref26">26</xref>] .</p><p>H 2 O 2 + HO &#183; → H 2 O + HO 2 &#183; (18)</p><p>HO 2 &#183; + HO &#183; → H 2 O + O 2 (19)</p><p>In this work, the process for addition of Fe(II) in concentration 1 &#215; 10<sup>−4</sup> M to the dye solution with presence ZnO has a negative effect. So, E% of this reaction declines to be 43.750. That belongs on the reacted of Fe<sup>2+</sup> with Perhydroxyl radical, according to the following equation [<xref ref-type="bibr" rid="scirp.78973-ref28">28</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref29">29</xref>] .</p><p>HO 2 &#183; + Fe 2 + → HO 2 − + Fe 3 + (20)</p><p>HO 2 &#183; + Fe 2 + → O 2 + Fe 3 + + H + (21)</p><p>From the other hand, the used of fenton’s reaction in the conditions of the photoreaction, that leads to depress the E% to 36.363. The certain concentration of H<sub>2</sub>O<sub>2</sub> and Fe<sup>2+</sup> causes to produce H<sub>2</sub>O and O<sub>2</sub> [<xref ref-type="bibr" rid="scirp.78973-ref30">30</xref>] [<xref ref-type="bibr" rid="scirp.78973-ref31">31</xref>] .</p><disp-formula id="scirp.78973-formula31"><graphic  xlink:href="//html.scirp.org/file/10-2170505x29.png"  xlink:type="simple"/></disp-formula><p>Scheme 1. Suggested mechanism for decolorization of Negrisone in suspension solution of ZnO.</p><p>Fe 2 + + H 2 O 2 → Fe 3 + + HO &#183; + HO − (22)</p><p>H 2 O 2 + HO &#183; → H 2 O + HO 2 &#183; (23)</p><p>HO 2 &#183; + HO &#183; → H 2 O + O 2 (24)</p></sec><sec id="s3_4"><title>3.4. Proposed Mechanism</title><p>The suggested mechanism for decolorization of Nigreson in presence ZnO under UV-A light was summarized in (Scheme 1).</p></sec><sec id="s3_5"><title>3.5. Conclusions</title><p>The essential conclusions for this work were proven the following results:</p><p>1) The photoreaction of decolorization of Nigresoin dye in suspension solution of ZnO obeys the pseudo first order kinetics.</p><p>2) The Rate of photocatalytic decolorization of the above dye is followed the next sequences:</p><p>Rate of decolorization in presence ZnO alone &gt; Rate of decolorization in presence ZnO with H<sub>2</sub>O<sub>2</sub> &gt; Rate of decolorization in presence ZnO with Fe(II) &gt; Rate of decolorization in presence ZnO with H<sub>2</sub>O<sub>2</sub> and Fe(II).</p><p>3) The decolorization reaction is fast, exothermic and spontaneously at initial pH 8.177 of dye solution.</p><p>4) At 25 min and 288.15 K, the efficiency (E%) of removal Nigrosin dye in presence of ZnO was reached to maximum value and to be 99.014.</p></sec></sec><sec id="s4"><title>Cite this paper</title><p>Jaafar, M.T. (2017) UV-A Activated ZnO Mediated Photocatalytic Decolorization of Nigrosine (Acid Black 2) Dye in Aqueous Solution. Journal of Geoscience and Environment Protection, 5, 138-147. https://doi.org/10.4236/gep.2017.59010</p></sec></body><back><ref-list><title>References</title><ref id="scirp.78973-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Babi&amp;#269, J. and Pavko, A. (2007) Production of Ligninolytic Enzymes by Ceriporiopsis Subvertmispora for Decolourization of Synthetic Dyes. 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