<?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">MSCE</journal-id><journal-title-group><journal-title>Journal of Materials Science and Chemical Engineering</journal-title></journal-title-group><issn pub-type="epub">2327-6045</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/msce.2017.510002</article-id><article-id pub-id-type="publisher-id">MSCE-79889</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Chemistry&amp;Materials Science</subject></subj-group></article-categories><title-group><article-title>
 
 
  Synthesis of CuO&lt;sub&gt;x&lt;/sub&gt;/MnO&lt;sub&gt;2&lt;/sub&gt; Heterostructures with Enhanced Visible Light-Driven Photocatalytic Activity
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Tao</surname><given-names>Yu</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Yangang</surname><given-names>Sun</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Cui</surname><given-names>Zhe</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Wei</surname><given-names>Wang</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Pinhua</surname><given-names>Rao</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib></contrib-group><aff id="aff2"><addr-line>College of Chemistry and Chemical Engineering, Shanghai University of Engineering Science, Shanghai, China</addr-line></aff><aff id="aff1"><addr-line>School of Materials Engineering, Shanghai University of Engineering Science, Shanghai, China</addr-line></aff><author-notes><corresp id="cor1">* E-mail:<email>syg021@sues.edu.cn(YS)</email>;<email>wangwei200173@sina.com(WW)</email>;<email>raopinhua@hotmail.com(PR)</email>;</corresp></author-notes><pub-date pub-type="epub"><day>25</day><month>10</month><year>2017</year></pub-date><volume>05</volume><issue>10</issue><fpage>12</fpage><lpage>25</lpage><history><date date-type="received"><day>22,</day>	<month>September</month>	<year>2017</year></date><date date-type="rev-recd"><day>24,</day>	<month>October</month>	<year>2017</year>	</date><date date-type="accepted"><day>27,</day>	<month>October</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>
 
 
  Organic pollutants coming from various industry processes are harmful to the environment, and semiconductor heterostructure is a promising candidate catalyst for poisonous wastewater treatment in the future. In this study, CuO
  <sub>x</sub>/MnO
  <sub>2</sub> heterostructures were successfully constructed, using a facile and effective hydrothermal method and chemical both/calcination route, which exhibited higher photocatalytic activity towards the photodegradation of organic contaminants under visible-light driven irradiation. The resulting CuO
  <sub>x</sub>/MnO
  <sub>2</sub> heterostructures were systematically characterized using various microscopic and spectroscopic techniques. Morphological characterizations show that the CuO
  <sub>x</sub> nanoparticles are well anchored on the surface of the MnO
  <sub>2</sub> nanowires (NMs). The photocatalytic activity enhancement of the CuO
  <sub>x</sub>/MnO
  <sub>2</sub> heterostructures (M-4) could be ascribed to the introduction of CuO
  <sub>x</sub> on the surface of MnO
  <sub>2</sub> NWs and the efficient separation of the electron-hole pairs compared to other CuO
  <sub>x</sub>/MnO
  <sub>2</sub> heterostructures and pure MnO
  <sub>2</sub> NMs. These results show that CuO
  <sub>x</sub>/MnO
  <sub>2</sub> heterostructures can be a suitable candidate for efficient visible light photocatalysts.
 
</p></abstract><kwd-group><kwd>CuO&lt;sub&gt;x&lt;/sub&gt;/MnO&lt;sub&gt;2&lt;/sub&gt; Heterostructures</kwd><kwd> Hydrothermal Method</kwd><kwd> Chemical Both/Calcination Route</kwd><kwd> Photocatalytic Activity</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Organic pollutants coming from various processes in industries are harmful to the environment, hazardous to human health due to their toxicity and persistence [<xref ref-type="bibr" rid="scirp.79889-ref1">1</xref>] [<xref ref-type="bibr" rid="scirp.79889-ref2">2</xref>] , which has aroused great concern worldwide. Many treatment approaches have been investigated for the removal of organic pollutants from wastewater including adsorption, chemical oxidation, biological degradation, ultrasound degradation and photocatalytic degradation [<xref ref-type="bibr" rid="scirp.79889-ref3">3</xref>] . Among them, photochemical degradation has been commonly suggested as a cost effective method for the degradation of many toxic organic pollutants from aqueous systems because of its low cost, simplicity and high efficiency [<xref ref-type="bibr" rid="scirp.79889-ref4">4</xref>] [<xref ref-type="bibr" rid="scirp.79889-ref5">5</xref>] . It is a universally acknowledged truth that the high performance catalysts play important roles in photocatalytic degradation application [<xref ref-type="bibr" rid="scirp.79889-ref6">6</xref>] [<xref ref-type="bibr" rid="scirp.79889-ref7">7</xref>] . Thus, designing and developing the high performance catalysts should be a key point to solve organic pollution in wastewater.</p><p>As a promising photocatalyst, manganese dioxide (MnO<sub>2</sub>) has attracted intensive interest due to its mass of merits like low-cost, environmental compatibility, abundant availability, strong adsorption and oxidation ability [<xref ref-type="bibr" rid="scirp.79889-ref8">8</xref>] - [<xref ref-type="bibr" rid="scirp.79889-ref15">15</xref>] . But the photocatalytic activity of MnO<sub>2</sub> is still restricted by the slow rate of charge transfer and high recombination probability of photogenerated electron-hole pairs. Many efforts have been made to improve the photocatalytic capability of MnO<sub>2</sub>, a large number of studies showed that MnO<sub>2</sub> combined with the conductor or semiconductor can effectively improve the photocatalytic activity compared to pure nanostructures. For example, Saravanakumar et al. [<xref ref-type="bibr" rid="scirp.79889-ref16">16</xref>] constructed Ag@MnO<sub>2</sub> nanowires, using a one step hydrothermal method, which exhibited excellent efficiency towards the photodegradation of organic contaminants under visible-light driven irradiation compared to pure MnO<sub>2</sub>. Zheng et al. [<xref ref-type="bibr" rid="scirp.79889-ref17">17</xref>] obtained hybrid 3D Co<sub>3</sub>O<sub>4</sub>@MnO<sub>2</sub> heterostructures by a facile and highly efficient solution-based method on nickel foam, and the as-synthesized 3D Co<sub>3</sub>O<sub>4</sub>@MnO<sub>2</sub> heterostructures exhibited remarkable photocatalytic activity and recycling stability for the degradation of organic dyes. A flower-like MnO<sub>2</sub>/BiOI composite [<xref ref-type="bibr" rid="scirp.79889-ref18">18</xref>] has been fabricated by a simple and cost-effective approach and demonstrated a photocatalytic degradation efficiency of 97.8% under visible light and 93.4% under simulated solar light irradiation for methyl orange (MO) within 40 min.</p><p>We noted that copper oxides as a photocatalyst hold great potential due to their unique optical and charge transport properties [<xref ref-type="bibr" rid="scirp.79889-ref19">19</xref>] [<xref ref-type="bibr" rid="scirp.79889-ref20">20</xref>] [<xref ref-type="bibr" rid="scirp.79889-ref21">21</xref>] [<xref ref-type="bibr" rid="scirp.79889-ref22">22</xref>] . Cu<sub>2</sub>O and CuO both are suitable for visible light absorption because of their favorable bandgap values that range from 1.7 to 2.6 eV [<xref ref-type="bibr" rid="scirp.79889-ref23">23</xref>] [<xref ref-type="bibr" rid="scirp.79889-ref24">24</xref>] . On the other hand, Zhou et al. [<xref ref-type="bibr" rid="scirp.79889-ref25">25</xref>] and Chen et al. [<xref ref-type="bibr" rid="scirp.79889-ref26">26</xref>] separately reported excellent photocatalytic activity of Cu<sub>2</sub>O/Cu nanocomposites and Cu/Cu<sub>2</sub>O core-shell nanowires for dye degradations of MO and methylene blue (MB).</p><p>Inspired by these previous reports, here we have synthesized CuO<sub>x</sub> nanoparticle/MnO<sub>2</sub> nanowire heterostructures, via a hydrothermal method followed by a facile and effective chemical both/calcination route. The photocatalytic activity of the CuO<sub>x</sub>/MnO<sub>2</sub> nanowire heterostructures was investigated under the irradiation of visible light, and they displayed high performance and stability for the photodecomposition of MB.</p></sec><sec id="s2"><title>2. Experimental Section</title><sec id="s2_1"><title>2.1. Synthesis of MnO<sub>2</sub> Nanowires</title><p>All of the chemicals were of analytical purity and used as received without further purification. MnO<sub>2</sub> nanowires (NWs) were prepared by a simple hydrothermal method. Firstly, the 1.715 g KMnO<sub>4</sub> was dissolved in 25 mL of deionized water under magnetic stirring, and 2.5 mL concentrated HCl was added dropwise into the above solution. The mixture of the solution was stirred continuously for 1 h. Secondly, the mixed solution was transferred into a 50 mL Teflon-lined stainless steel autoclave and heated in an oven at 180˚C for 12 h. After the reaction, the autoclave was cooled down to room temperature in air, the sample was then collected by filtration and washed with ethanol and deionized water several times, and dried at 80˚C for 3 h. Finally, the dried sample was further calcined at 500˚C for 1 hour under N<sub>2</sub> environment, and MnO<sub>2</sub> NWs were obtained.</p></sec><sec id="s2_2"><title>2.2. Synthesis of CuO<sub>x</sub>/MnO<sub>2</sub> Heterostructures</title><p>CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures were synthesized by a simple chemical both and calcination method. Firstly, the 0.174 g of the obtained MnO<sub>2</sub> NWs were dispersed in 50 mL deionized water followed by stirring for 10 min, then 0.72 g of glucose was dissolved in the above solution under the same conditions, 0.2 g of Cu(AC)<sub>2</sub>・H<sub>2</sub>O was added to the mixed solution of MnO<sub>2</sub> NWs and glucose while keeping stirring for 10 min, then the obtained mixed solution was heated in water-bath for 1 hours at 90˚C. Secondly, the product was collected and washed by filtration at room temperature, and dried at 50˚C overnight. Thirdly, the collected solid powders were put into a tubular furnace and heated to 500˚C at a rate of 5˚C・min<sup>−1</sup> and maintained for 180 min under N<sub>2</sub> protection. Finally, the CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures were obtained and named as the sample M-2. By adjusting the amount of Cu(AC)<sub>2</sub>・H<sub>2</sub>O, a series of CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures using 0.3 and 0.4 g of Cu(AC)<sub>2</sub>・H<sub>2</sub>O were obtained and denoted as M-3 and M-4, respectively. The synthesis of the CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures is shown in <xref ref-type="fig" rid="fig1">Figure 1</xref>.</p></sec><sec id="s2_3"><title>2.3. Characterization</title><p>X-Ray power diffraction (XRD) patterns were recorded on a Rigaku D/max-2550 PC X-ray power diffractometer employing Cu-K a radiation operating at 40 kV and 200 mA. The morphology of the samples was observed using a field emission scanning electron microscope (SEM, S-4800) at an acceleration voltage of 5</p><p>kV. The UV-vis diffuse reflectance spectra (DRS) of the sample were performed on a Perkin Elmer Lambda 35 spectrophotometer, using BaSO<sub>4</sub> as reference. The photoluminescence (PL) emission spectra of the samples were obtained using a fluorescence spectrophotometer (FS-5) at room temperature.</p></sec><sec id="s2_4"><title>2.4. Photocatalyst Activity Texts</title><p>The photocatalytic activities of the as-prepared samples were evaluated using the degradation of methylene blue (MB) at room temperature under visible light irradiation. In photocatalytic experiment, 20 mg photocatalysts was suspended in 50 mL of MB solutions (5 mg・L<sup>−1</sup>). Before lighting on, the suspension was stirred for 30 min in the dark to ensure absorption-desorption equilibrium between the photocatalyst and organic dye solution. After that, the suspension under magnetic stirring was placed approximately 20 cm below a xenon lamp (500 W, Model PLS-SXE300) with a cut-off filter that only emits visible light (λ &gt; 400 nm). At a given time period, the 3 mL suspension was removed from the original solution and centrifuged at 8000 rpm for 3 min to remove the remnant photocatalyst, The absorbance of MB concentration were analyzed by a UV-vis spectrophotometer (UV-2550, Shimadzu) at wavelength 664 nm. After testing, the suspension was returned and the irradiation was resumed. Consequently, the degradation rate for MB could be calculated according to the change of the absorbance.</p></sec></sec><sec id="s3"><title>3. Results and Discussion</title><sec id="s3_1"><title>3.1. Preparation and Characterization of Catalysts</title><p>CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures with different amount of Cu(AC)<sub>2</sub>・H<sub>2</sub>O (0.2 g, 0.3 g and 0.4 g) were prepared via a simple chemical both and calcination method. MnO<sub>2</sub> NWs were produced by a reaction of KMnO<sub>4</sub> and concentrated HCl and then crystallized during the hydrothermal process. Meanwhile Cu<sup>2+</sup> and glucose were deposited onto the surface of MnO<sub>2</sub> NWs. The conversion of CuO<sub>x</sub> from Cu<sup>2+</sup> was achieved by the subsequent calcination process under N<sub>2</sub> protection. The resulting catalysts are named as M-2, M-3 and M-4, respectively.</p><p>The phase of CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures was analyzed using the XRD measurements. <xref ref-type="fig" rid="fig2">Figure 2</xref> presents the XRD patterns of the pure MnO<sub>2</sub> NWs, M-2, M-3 and M-4. In the XRD pattern of the pure MnO<sub>2</sub> NWs, all diffraction peaks at the 2θ values of 12.7˚, 18.0˚, 28.8˚, 37.5˚, 38.8˚, 41.9˚, 49.8˚, 56.1˚, 60.1˚, 65.3˚ and 69.3˚ correspond to the (110), (200), (310), (211), (330), (301), (411), (660), (521), (002) and (541) crystal faces of α-MnO<sub>2</sub> (JCPDS Card No: 44-0141), respectively. No impurity peaks are found within experimental error, indicating a high purity of α-MnO<sub>2</sub>. In the XRD pattern of M-2, three characteristic peaks with 2θ values of 32.3˚, 35.8˚ and 57.5˚ are attributed to the (110), (11-1) and (202) crystal planes [<xref ref-type="bibr" rid="scirp.79889-ref27">27</xref>] of CuO (JCPDS Card No: 048-1548), and the peaks with 2θ values of 30.5˚, 37.5˚ and 62.9˚ could be indexed to the (110), (111) and (220) crystal planes of Cu<sub>2</sub>O (JCPDS Card No: 78-2076), respectively. The Cu<sub>2</sub>O (111)</p><p>peak is very close to the MnO<sub>2</sub> (211) peak and thus they are overlapped at around 37.5 in the pattern, and the other peaks can be indexed to MnO<sub>2</sub>. Compared with the pure MnO<sub>2</sub> NWs, the intensity of MnO<sub>2</sub> diffraction peaks obviously decreases in the XRD pattern of M-2. Thus, according to the XRD results, the sample M-2 is consisted of three phases of CuO, Cu<sub>2</sub>O and MnO<sub>2</sub>, indicating that the information of CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures. In the XRD pattern of M-3, we can clearly see that there are four characteristic peaks with 2θ values of 32.3˚, 35.8˚, 38.7˚ and 57.5˚ corresponding to the (110), (111), (11-1) and (202) crystal planes of CuO, respectively, Three peaks with 2θ values of 30.5˚, 37.5˚ and 62.9˚ correspond to the (110), (111) and (220) crystal planes of Cu<sub>2</sub>O, and one peak with 2θ value of 43.0˚ is assigned to the (111) crystal planes of Cu (JCPDS Card No: 04-0836) [<xref ref-type="bibr" rid="scirp.79889-ref28">28</xref>] , and the other peaks can be indexed to MnO<sub>2</sub>. The intensity of MnO<sub>2 </sub>diffraction peaks in the XRD pattern of M-3 was weaker than one in the XRD pattern of M-2. According to the XRD results, the sample M-3 is composed of four phases of CuO, Cu<sub>2</sub>O, Cu and MnO<sub>2</sub>, indicating that the information of CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures. In the XRD pattern of M-4, we can also clearly see there are two peaks at around 43.0˚ and 50.1˚ corresponding to the (111) and (200) crystal planes of Cu, and two peaks at around 35.8˚ and 61.2˚ are attributed to the (002) and (113) crystal planes of CuO, and one peak at 40.5˚ is consistent with the (200) crystal planes of Cu<sub>2</sub>O. No peaks of MnO<sub>2</sub> are found due to the loading of CuO<sub>x</sub>. So the sample M-4 is composed of four phases of CuO, Cu<sub>2</sub>O, Cu and MnO<sub>2</sub>. The above results verify the formation of CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures.</p></sec><sec id="s3_2"><title>3.2. SEM Images of the Pure MnO<sub>2</sub> NWs, M-2, M-3 and M-4</title><p>The morphology of MnO<sub>2</sub> NWs, M-2, M-3 and M-4 was observed in scanning electron microscopy (SEM) images, which are shown in <xref ref-type="fig" rid="fig3">Figure 3</xref>. <xref ref-type="fig" rid="fig3">Figure 3</xref>(a) and b are the SEM images of the pure MnO<sub>2</sub> NWs with different magnifications.</p><p>It can be clearly seen that the pure MnO<sub>2</sub> NWs with diameters of about 30 - 80 nm and lengths of 2 - 3 um have a relatively smooth surface, and MnO<sub>2</sub> NWs were uniform in diameter through the entire length and gathered in disorder. As can be seen from <xref ref-type="fig" rid="fig3">Figure 3</xref>(c) and <xref ref-type="fig" rid="fig3">Figure 3</xref>(d), a small and sparse nanoparticles with the sizes of 10 - 20 nm were deposited on the surface of MnO<sub>2</sub> NWs in the sample M-2 prepared using 0.2 g of Cu(AC)<sub>2</sub>・H<sub>2</sub>O. When increasing the amount of Cu(AC)<sub>2</sub>・H<sub>2</sub>O to 0.3 g in the sample M-3, as shown in <xref ref-type="fig" rid="fig3">Figure 3</xref>(e) and <xref ref-type="fig" rid="fig3">Figure 3</xref>(f), the sizes of nanoparticles on the surfaces of MnO<sub>2</sub> NWs increase to 20 - 40 nm. Using 0.4 g of Cu(AC)<sub>2</sub>・H<sub>2</sub>O in the sample M-4 (<xref ref-type="fig" rid="fig3">Figure 3</xref>(g) and <xref ref-type="fig" rid="fig3">Figure 3</xref>(h)), the bigger and more nanoparticles with diameters of 20 - 50 nm were deposited on the surfaces of MnO<sub>2</sub> NWs, and the surface of MnO<sub>2</sub> NWs is obviously rough. Additionally, it can not be observed the more density of nanoparticles grown on the surface of MnO<sub>2</sub> NWs with increasing the amount of Cu(AC)<sub>2</sub>・H<sub>2</sub>O to 0.5 g. These nanoparticles are considered to be the composite of CuO<sub>x</sub>. So, a series of CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures of the sample M-2, M-3 and M-4 were successfully fabricated by changing the amount of Cu(AC)<sub>2</sub>・H<sub>2</sub>O.</p><p>We investigate the optical properties of the pure MnO<sub>2</sub> NWs and CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures using a combination of UV-vis and PL technologies. <xref ref-type="fig" rid="fig4">Figure 4</xref>(a) shows the UV-vis absorbance spectra of the pure MnO<sub>2</sub> NWs and CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures (M-2, M-3 and M-4). From the spectra, the characteristic absorption peak of the pure MnO<sub>2</sub> NWs is at 450 nm and the absorption band edge enlarges to almost the full visible region [<xref ref-type="bibr" rid="scirp.79889-ref29">29</xref>] . The sample M-2 and M-3 of</p><p>the CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures show two broad bands at 400 - 460 nm and 650 - 700 nm. With the increase of the amount of Cu(AC)<sub>2</sub>・H<sub>2</sub>O, the absorption intensity of the sample M-2 and M-3 was enhanced gradually, which further confirms that Cu<sup>2+</sup> had been successfully anchored on the surface of the MnO<sub>2</sub> NWs. In comparison with the sample M-2 and M-3, the sample M-4 shows a broad and strong absorption in visible light range (400 - 700 nm), and the band gap energy (E<sub>g</sub>) of the sample M-4 calculated on the basis of the corresponding absorption edge was 1.57 eV, showing a significant red-shift compared with the pure MnO<sub>2</sub> NWs. It suggested that the sample M-4 might display good photocatalytic activity under visible light.</p><p>The photoluminescence (PL) spectra were characterized the trapping, migration and separation of electron-hole pairs, and the lower PL intensity indicates the higher photocatalytic properties of the nanomaterials [<xref ref-type="bibr" rid="scirp.79889-ref30">30</xref>] . The PL spectrum of the samples is measured at room temperature using 300 nm as an excitation wavelength (<xref ref-type="fig" rid="fig4">Figure 4</xref>(b)). It is clear that two strong emission peaks of the pure MnO<sub>2</sub> NWs are at about 349 and 351 nm and it is similar to the emission peaks of M-3. Compared with the emission peaks of the pure MnO<sub>2</sub> NWs and M-3, the PL spectra of M-2 and M-4 consist of two weak emission peaks located at about 348 nm and 353 nm and two weaker emission peaks at 412 nm and 453 nm [<xref ref-type="bibr" rid="scirp.79889-ref31">31</xref>] [<xref ref-type="bibr" rid="scirp.79889-ref32">32</xref>] .<sup> </sup>The sample M-4 among all the samples showed the lowest PL emission intensity and indicated the enhancement of photocatalytic performance.</p></sec><sec id="s3_3"><title>3.3. Photocatalytic Activity</title><p>To evaluate the photocatalytic activity of the as-synthesized CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures, the degradation of MB (methylene blue, a standard organic dye) under visible light radiation is utilized as a probe reaction, and displays a characteristic absorption of MB at a wavelength of around 664 nm in absorption spectra. For comparison, the photocatalytic experiment using the pure MnO<sub>2</sub> NWs as the catalyst is also conducted under the same condition. One thing to note here is that before irradiation the mixed solution of the photocatalysts and MB is stirred for 30 min in the dark to establish the adsorption/desorption equilibrium on the photocatalyst surfaces. The corresponding photocatalytic properties have been demonstrated in <xref ref-type="fig" rid="fig5">Figure 5</xref>. <xref ref-type="fig" rid="fig5">Figure 5</xref>(a) shows the temporal evolution of the absorption spectra of MB over the sample M-4. The characteristic absorption peak of MB at wavelength of 664 nm decreases sharply as the reaction time increases and almost disappears after 140 min, confirming that MB can be efficiently degraded by the sample M-4. <xref ref-type="fig" rid="fig5">Figure 5</xref>(b) presents the degradation curves of MB over different catalysts. When using the pure MnO<sub>2</sub> NWs as the photocatalyst, only 47.2% of MB is degraded due to the fast recombination rate of charge carriers, resulting from the narrow band gap [<xref ref-type="bibr" rid="scirp.79889-ref18">18</xref>] . Interestingly, all the CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures (M-2, M-3 and M-4) display higher activities than the pure MnO<sub>2</sub> NWs, and the MB degradation efficiencies reach up to 69.3%, 89.2% and 96.1%, respectively. It is obvious that the photocatalytic activity of the pure MnO<sub>2</sub> NWs is improved due to different amount of CuO<sub>x</sub> was loaded on the surface of MnO<sub>2</sub> NWs. This may be ascribed to a large specific surface area which can introduce more unsaturated coordination sites in the surface that exposed to MB molecules, that is more favorable for the photocatalytic degradation of MB molecules [<xref ref-type="bibr" rid="scirp.79889-ref33">33</xref>] .</p><p>In order to better understand the photocatalytic efficiency of the catalysis, the curve of ln(C<sub>0</sub>/C) versus time of MB photodegradation process was also investigated. On the basis of the Langmuir-Hinshelwood model, the linear relationship of ln(C<sub>0</sub>/C) versus time can be described as: −ln(C<sub>0</sub>/C) = kt, where k represents the reaction rate constant of the pseudo-first-order. <xref ref-type="fig" rid="fig6">Figure 6</xref> shows the effect of different samples on the kinetics of MB under visible light irradiation. The value of apparent rate constant k, which is equal to the corresponding slope of the simulation curve, is shown in the inset of <xref ref-type="fig" rid="fig6">Figure 6</xref> in the form of a histogram graph. It can be seen that the k values for the pure MnO<sub>2</sub> NWs, M-2, M-3 and</p><p>M-4 are 0.005 min<sup>−1</sup>, 0.015 min<sup>−1</sup>, 0.008 min<sup>−1</sup> and 0.021 min<sup>−1</sup>, respectively. These results show the introduction of CuO<sub>x</sub> improve the visible light photocatalytic performance of the MnO<sub>2</sub> NWs and the sample M-4 exhibits the highest photodegraded efficiency.</p><p>The stability and reusability of photocatalysts is another important consideration for their practical applications. Therefore, MB recycling degradation experiments over the sample M-4 were also conducted. <xref ref-type="fig" rid="fig7">Figure 7</xref> shows the degradation efficiencies of MB in three cycles, the first degradation rate of MB was 93.73% and 84.35% for the second time. After repeating the procedure 3 times, the degradation rate still remained at 84.07%, and there is a slight loss of photocatalytic activity, demonstration the good recyclability of M-4. This result indicates that the sample M-4 can still remain stable and efficient during organic dye degradation. Comparing these samples, the sample M-4 has better degradation</p><p>activity, which indicates CuO<sub>x</sub> nanoparticles on the surface of MnO<sub>2</sub> nanowires played key roles in the enhanced photocatalytic performance. The enhancement may be due to the following reasons. Firstly, the higher photocatalysis efficiency of the heterostructure samples could be explained in terms of the enhancement of UV-vis absorbance spectra and the weaker PL emissions due to CuO<sub>x</sub> nanoparticle depositions. Secondly, CuO<sub>x</sub> nanoparticles on the surface of CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures have the increase of surface area, and inhibit the recombination of electron-hole pairs caused by electronic conduction of Cu nanoparticles [<xref ref-type="bibr" rid="scirp.79889-ref34">34</xref>] .</p></sec></sec><sec id="s4"><title>4. Conclusion</title><p>In summary, CuO<sub>x</sub>/MnO<sub>2</sub> heterostructure photocatalyst was successfully synthesized through a facile and effective hydrothermal method and chemical both/calcination route. For the sample M-2 of CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures, CuO<sub>x</sub> is composed of two phases of CuO and Cu<sub>2</sub>O, and for the sample M-3 and M-4 of CuO<sub>x</sub>/MnO<sub>2</sub> heterostructures, CuO<sub>x</sub> is consisted of three phases of CuO, Cu<sub>2</sub>O and Cu. The sample M-4 in the degradation of MB under visible light showed enhanced photocatalytic activity compared to M-2, M-3 and pure MnO<sub>2</sub> NWs. The enhanced photocatalytic performance can be attributed to the introduction of CuO<sub>x</sub> on the surface of MnO<sub>2</sub> NWs and the efficient separation of the electron-hole pairs. The present study thus offers a facile and efficient synthesis method and a promising candidate catalyst for poisonous wastewater treatment in the near future.</p></sec><sec id="s5"><title>Acknowledgements</title><p>This research was supported by the Foundation of Shanghai University of Engineering Science (Grant No. 2012gp13, E1-0501-15-0105), Innovation Program of Shanghai Municipal Education Commission (Grant No. 14ZZ160), Open Fund of State Key Laboratory for Modification of Chemical Fibers and Polymer Materials, Donghua University (Grant No. LK1209).</p></sec><sec id="s6"><title>Cite this paper</title><p>Yu, T., Sun, Y.G., Zhe, C., Wang, W. and Rao, P.H. (2017) Synthesis of CuO<sub>x</sub>/MnO<sub>2</sub> Heterostructures with Enhanced Visible Light-Driven Photocatalytic Activity. Journal of Materials Science and Chemical Engineering, 5, 12-25. https://doi.org/10.4236/msce.2017.510002</p></sec></body><back><ref-list><title>References</title><ref id="scirp.79889-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">Wang, H.L., Zhang, L.S., Chen, Z.G., Hu, J.Q., Li, S.J., Wang, Z.H., Liu, J.S. and Wang, X.C. (2014) Semiconductor Heterojunction Photocatalysts: Design, Construction, and Photocatalytic Performances. Chemical Society Reviews, 43, 5234-5244. https://doi.org/10.1039/C4CS00126E</mixed-citation></ref><ref id="scirp.79889-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">Liu, Y., Luo, C., Sun, J., Li, H., Sun, Z. and Yan, S. (2015) Enhanced Adsorption Removal of Methyl Orange from Aqueous Solution by Nanostructured Proton-Containing δ-MnO2. Journal of Materials Chemistry A, 3, 5674-5682. https://doi.org/10.1039/C4TA07112C</mixed-citation></ref><ref id="scirp.79889-ref3"><label>3</label><mixed-citation publication-type="other" xlink:type="simple">Qu, J., Shi, L., He, C., Gao, F., Li, B., Zhou, Q., Hu, H., Shao, G., Wang, X. and Qiu, J. (2014) Highly Efficient Synthesis of Graphene/MnO2 Hybrids and Their Application for Ultrafast Oxidative Decomposition of Methylene Blue. Carbon, 66, 485-492. https://doi.org/10.1016/j.carbon.2013.09.025</mixed-citation></ref><ref id="scirp.79889-ref4"><label>4</label><mixed-citation publication-type="other" xlink:type="simple">Sang, L.X., Zhao, Y.X. and Burda, C. (2014) TiO2 Nanoparticles as Functional Building Blocks. Chemical Reviews, 114, 9283-9318. https://doi.org/10.1021/cr400629p</mixed-citation></ref><ref id="scirp.79889-ref5"><label>5</label><mixed-citation publication-type="other" xlink:type="simple">Chen, X.B., Liu, L., Yu, P.Y. and Mao, S.S. (2011) Increasing Solar Absorption for Photocatalysis with Black Hydrogenated Titanium Dioxide Nanocrystals. Science, 331, 746-750. https://doi.org/10.1126/science.1200448</mixed-citation></ref><ref id="scirp.79889-ref6"><label>6</label><mixed-citation publication-type="other" xlink:type="simple">Marschall, R. (2014) Semiconductor Composites: Strategies for Enhancing Charge Carrier Separation to Improve Photocatalytic Activity. Advanced Functional Materials, 24, 2421-2440. https://doi.org/10.1002/adfm.201303214</mixed-citation></ref><ref id="scirp.79889-ref7"><label>7</label><mixed-citation publication-type="other" xlink:type="simple">Tong, H., Ouyang, S.X., Bi, Y.P., Umezawa, N., Oshikiri, M. and Ye, J.H. (2012) Nano-Photocatalytic Materials: Possibilities and Challenges. Advanced Materials, 24, 229-251. https://doi.org/10.1002/adma.201102752</mixed-citation></ref><ref id="scirp.79889-ref8"><label>8</label><mixed-citation publication-type="other" xlink:type="simple">Zhao, H., Zhang, G. and Zhang, Q. (2014) MnO2/CeO2 for Catalytic Ultrasonic Degradation of Methyl Orange. Ultrasonics Sonochemistry, 21, 991-996. https://doi.org/10.1016/j.ultsonch.2013.12.002</mixed-citation></ref><ref id="scirp.79889-ref9"><label>9</label><mixed-citation publication-type="other" xlink:type="simple">Gao, F.Y., Tang, X.L., Yi, H.H., Chu, C., Li, N., Li, J.Y. and Zhao, S.Z. (2017) In-Situ DRIFTS for the Mechanistic Studies of NO Oxidation over α-MnO2, β-MnO2 and β-MnO2 Catalysts. Chemical Engineering Journal, 322, 525-537. https://doi.org/10.1016/j.cej.2017.04.006</mixed-citation></ref><ref id="scirp.79889-ref10"><label>10</label><mixed-citation publication-type="other" xlink:type="simple">Li, D.K. and Guo, Z.G. (2017) Stable and Self-Healing Superhydrophobic MnO2@ Fabrics: Applications in Self-Cleaning, Oil/Water Separation and Wear Resistance. Journal of Colloid and Interface Science, 503, 124-130. https://doi.org/10.1016/j.jcis.2017.05.015</mixed-citation></ref><ref id="scirp.79889-ref11"><label>11</label><mixed-citation publication-type="other" xlink:type="simple">Zhao, D., Yang, X., Zhang, H., Chen, C. and Wang, X. (2010) Effect of Environmental Conditions on Pb (II) Adsorption on β-MnO2. Chemical Engineering Journal, 164, 49-55.</mixed-citation></ref><ref id="scirp.79889-ref12"><label>12</label><mixed-citation publication-type="other" xlink:type="simple">Singh, M., Thanh, D.N., Ulbrich, P., Strnadová, N. and Stěpánek, F. (2010) Synthesis, Characterization and Study of Arsenate Adsorption from Aqueous Solution by α- and β-Phase Manganese Dioxide Nanoadsorbents. Journal of Solid State Chemistry, 183, 2979-2986.</mixed-citation></ref><ref id="scirp.79889-ref13"><label>13</label><mixed-citation publication-type="other" xlink:type="simple">Wang, Q.F., Xu, J., Wang, X.F., Liu, B., Hou, X.J., Yu, G., Chen, D. and Shen, G.Z. (2014) Core-Shell CuCo2O4@MnO2 Nanowires on Carbon Fabrics as High-Performance Materials for Flexible, All-Solid-State, Electrochemical Capacitors. ChemElectroChem, 1, 559-564. https://doi.org/10.1002/celc.201300084</mixed-citation></ref><ref id="scirp.79889-ref14"><label>14</label><mixed-citation publication-type="other" xlink:type="simple">Li, W.Y., Li, G., Sun, J., Zou, R., Xu, K., Sun, Y., Chen, Z., Yang, J. and Hu, J.Q. (2013) Hierarchical Heterostructures of MnO2 Nanosheets or Nanorods Grown on Au-Coated Co3O4 Porous Nanowalls for High-Performance Pseudocapacitance. Nanoscale, 5, 2901-2908. https://doi.org/10.1039/c3nr34140b</mixed-citation></ref><ref id="scirp.79889-ref15"><label>15</label><mixed-citation publication-type="other" xlink:type="simple">Xiao, W., Wang, D. and Lou, X.W. (2010) Shape-Controlled Synthesis of MnO2 Nanostructures with Enhanced Electrocatalytic Activity for Oxygen Reduction. The Journal of Physical Chemistry C, 114, 1694-1700. https://doi.org/10.1021/jp909386d</mixed-citation></ref><ref id="scirp.79889-ref16"><label>16</label><mixed-citation publication-type="other" xlink:type="simple">Saravanakumar, K., Muthuraj, V. and Vadivel, S. (2016) Constructing Novel Ag Nanoparticles Anchored on MnO2 Nanowires as an Efficient Visible Light Driven Photocatalyst. RSC Advances, 6, 61357-61366. https://doi.org/10.1039/C6RA10444D</mixed-citation></ref><ref id="scirp.79889-ref17"><label>17</label><mixed-citation publication-type="other" xlink:type="simple">Zheng, X., Han, Z., Yang, W., Qu, F., Liu, B. and Wu, X. (2016) 3D Co3O4@MnO2 Heterostructures Grown on a Flexible Substrate and Their Applications in Supercapacitor Electrodes and Photocatalysts. Dalton Transactions, 45, 16850-16858. https://doi.org/10.1039/C6DT03076A</mixed-citation></ref><ref id="scirp.79889-ref18"><label>18</label><mixed-citation publication-type="other" xlink:type="simple">Liu, S., Liu, H., Jin, G. and Yuan, H. (2015) Preparation of Novel Flower-Like MnO2/BiOI Composite with Highly Enhanced Adsorption and Photocatalytic Activity. RSC Advances, 5, 45646-45653. https://doi.org/10.1039/C5RA02402A</mixed-citation></ref><ref id="scirp.79889-ref19"><label>19</label><mixed-citation publication-type="other" xlink:type="simple">Dorraj, M., Alizadeh, M., Sairi, N.A., Basirun, W.J., Goh, B.T., Woi, P.M. and Alias, Y. (2017) Enhanced Visible Light Photocatalytic Activity of Copper-Doped Titanium Oxide-Zinc Oxide Heterojunction for Methyl Orange Degradation. Applied Surface Science, 414, 251-261.</mixed-citation></ref><ref id="scirp.79889-ref20"><label>20</label><mixed-citation publication-type="other" xlink:type="simple">Zhang, W.L., Sun, Y.G., Xiao, Z.Y., Li, W.Y., Li, B., Huang, X.J., Liu, X.J. and Hu, J.Q. (2015) Heterostructures of CuS Nanoparticle/ZnO Nanorod Arrays on Carbon Fibers with Improved Visible and Solar Light Photocatalytic Properties. Journal of Materials Chemistry A, 3, 7304-7313. https://doi.org/10.1039/C5TA00560D</mixed-citation></ref><ref id="scirp.79889-ref21"><label>21</label><mixed-citation publication-type="other" xlink:type="simple">Huang, C., Long, Z., Miyauchi, M. and Qiu, X. (2014) A Facile One-Pot Synthesis of Cu-Cu2O Concave Cube Hybrid Architectures. CrystEngComm, 16, 4967-4972. https://doi.org/10.1039/C4CE00250D</mixed-citation></ref><ref id="scirp.79889-ref22"><label>22</label><mixed-citation publication-type="other" xlink:type="simple">Shi, H., Yu, K., Sun, F. and Zhu, Z. (2012) Controllable Synthesis of Novel Cu2O Micro/Nano-Crystals and Their Photoluminescence, Photocatalytic and Field Emission Properties. CrystEngComm, 14, 278-285. https://doi.org/10.1039/C1CE05868A</mixed-citation></ref><ref id="scirp.79889-ref23"><label>23</label><mixed-citation publication-type="other" xlink:type="simple">Yin, M., Wu, C.K., Lou, Y., Burda, C., Koberstein, J.T., Zhu, Y. and O’Brien, S. (2015) Copper Oxide Nanocrystals. Journal of the American Chemical Society, 127, 9506-9511.</mixed-citation></ref><ref id="scirp.79889-ref24"><label>24</label><mixed-citation publication-type="other" xlink:type="simple">https://doi.org/10.1021/ja050006u</mixed-citation></ref><ref id="scirp.79889-ref25"><label>25</label><mixed-citation publication-type="other" xlink:type="simple">Yu, H., Yu, J., Liu, S. and Mann, S. (2007) Template-Free Hydrothermal Synthesis of CuO/Cu2O Composite Hollow Microspheres. Chemistry of Materials, 19, 4327-4334. https://doi.org/10.1021/cm070386d</mixed-citation></ref><ref id="scirp.79889-ref26"><label>26</label><mixed-citation publication-type="other" xlink:type="simple">Zhou, B., Liu, Z., Wang, H., Yang, Y. and Su, W. (2009) Experimental Study on Photocatalytic Activity of Cu2O/Cu Nanocomposites under Visible Light. Catalysis Letters, 132, 75-80. https://doi.org/10.1007/s10562-009-0063-3</mixed-citation></ref><ref id="scirp.79889-ref27"><label>27</label><mixed-citation publication-type="other" xlink:type="simple">Chen, W., Fan, Z. and Lai, Z. (2013) Synthesis of Core-Shell Heterostructured Cu/Cu2O Nanowires Monitored by in Situ XRD as Efficient Visible-Light Photocatalysts. Journal of Materials Chemistry A, 1, 13862-13868. https://doi.org/10.1039/c3ta13413j</mixed-citation></ref><ref id="scirp.79889-ref28"><label>28</label><mixed-citation publication-type="other" xlink:type="simple">Basnet, P. and Zhao, Y.P. (2016) Tuning the CuxO Nanorod Composition for Efficient Visible Light Induced Photocatalysis. Catalysis Science &amp; Technology, 6, 2228-2238. https://doi.org/10.1039/C5CY01464F</mixed-citation></ref><ref id="scirp.79889-ref29"><label>29</label><mixed-citation publication-type="other" xlink:type="simple">Zhang, R.R., Hu, L., Bao, S.X., Li, R., Gao, L., Li, R. and Chen, Q.W. (2016) Surface Polarization Enhancement: High Catalytic Performance of Cu/CuOx/C Nanocomposites Derived from Cu-BTC for CO Oxidation. Journal of Materials Chemistry A, 4, 8412-8420. https://doi.org/10.1039/C6TA01199C</mixed-citation></ref><ref id="scirp.79889-ref30"><label>30</label><mixed-citation publication-type="other" xlink:type="simple">Xue, M., Huang, L., Wang, J.Q., Wang, Y., Gao, L., Zhu, J.H. and Zou, Z.G. (2008) The Direct Synthesis of Mesoporous Structured MnO2/TiO2 Nanocomposite: A Novel Visible-Light Active Photocatalyst with Large Pore Size. Nanotechnology, 19, 185604-185611. https://doi.org/10.1088/0957-4484/19/18/185604</mixed-citation></ref><ref id="scirp.79889-ref31"><label>31</label><mixed-citation publication-type="other" xlink:type="simple">Kumar, P.S., Selvakumar, M., Babu, S.G., Jaganathan, S.K., Karuthapandian, S. and Chattopadhyay, S. (2015) Novel CuO/Chitosan Nanocomposite Thin Film: Facile Hand-Picking Recoverable, Efficient and Reusable Heterogeneous Photocatalyst. RSC Advances, 5, 57493-57501. https://doi.org/10.1039/C5RA08783J</mixed-citation></ref><ref id="scirp.79889-ref32"><label>32</label><mixed-citation publication-type="other" xlink:type="simple">Huo, J.P., Fang, L.T., Lei, Y.L., Zeng, G.C. and Zeng, H.P. (2014) Facile Preparation of Yttrium and Aluminum Co-Doped ZnO via a Sol-Gel Route for Photocatalytic Hydrogen Production. Journal of Materials Chemistry A, 2, 11040-11044. https://doi.org/10.1039/C4TA02207F</mixed-citation></ref><ref id="scirp.79889-ref33"><label>33</label><mixed-citation publication-type="other" xlink:type="simple">John, R.E., Chandran, A., Thomas, M., Jose, J. and George, K.C. (2016) Surface-Defect Induced Modifications in the Optical Properties of α-MnO Nanorods. Applied Surface Science, 367, 43-51.</mixed-citation></ref><ref id="scirp.79889-ref34"><label>34</label><mixed-citation publication-type="other" xlink:type="simple">Li, H., Yu, K., Lei, X., Guo, B., Li, C., Fu, H. and Zhu, Z. (2015) Synthesis of MoS2@CuO Heterogeneous Structure with Improved Photocatalysis Performance and H2O Adsorption Analysis. Dalton Transactions, 44, 10438-10447. https://doi.org/10.1039/C5DT01125F</mixed-citation></ref><ref id="scirp.79889-ref35"><label>35</label><mixed-citation publication-type="other" xlink:type="simple">Yang, J.B., Li, Z., Zhao, C.X., Wang, Y. and Liu, X.Q. (2014) Facile Synthesis of Ag-Cu2O Composites with Enhanced Photocatalytic Activity. Materials Research Bulletin, 60, 530-536.</mixed-citation></ref></ref-list></back></article>