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硫摻雜氧化錫納米材料的固相合成及其可見光降解百草枯

2015-12-15 07:18賀仲兵劉少友閔宗義楊紅蕓
無機化學學報 2015年4期
關鍵詞:凱里百草晶格

賀仲兵 劉少友 閔宗義 楊紅蕓 聶 信

(1凱里學院化學與材料工程學院,凱里556011) (2湖南大學環(huán)境科學與工程學院,長沙432001)

(3廣西大學環(huán)境學院,南寧530004)

硫摻雜氧化錫納米材料的固相合成及其可見光降解百草枯

賀仲兵1,2劉少友*,1,3閔宗義2楊紅蕓1聶 信1

(1凱里學院化學與材料工程學院,凱里556011) (2湖南大學環(huán)境科學與工程學院,長沙432001)

(3廣西大學環(huán)境學院,南寧530004)

以十二烷基苯磺酸鈉(SDBS)為模板,采用低溫固相反應法合成了硫摻雜二氧化錫(S-SnO2)納米粉體材料,并用XRD、XPS、SEM、UV-Vis、FTIR及HR-TEM等技術對材料進行了表征,探討了S摻雜SnO2納米材料對百草枯的可見光降解性能,分析了S摻雜效應的作用機理。結果表明,采用固相反應法所得SnO2及S-SnO2納米材料的禁帶寬度變窄,SDBS對材料的表面結構具有一定的調控作用。S是以S/S和S/S的形式進入SnO2晶格形成Sn1-xSxO2晶體結構而不是進入SnO2晶格間隙,Sn-O-S鍵的彎曲振動峰介于930~980 cm-1之間。S的摻雜使SnO2納米材料表面活性增強,光催化降解百草枯的活性依次為SnO2

硫摻雜;二氧化錫;固相合成;可見光降解;百草枯

0 Introduction

Paraquat(1,1′-Dimethyl-4,4′-bipyridinium)is a quick-acting and non-selective contact herbicide,and it could kill green plant tissue on contact[1].It is highly toxic to human beings and animals,potentially leading to acute respiratory distress syndrome(ARDS),and there are no specific antidotes[2].It is also reported that paraquat may be considered as persistent organic pollutants as it could persist in soil for a long time (with a half-life up to 20 years)and accumulate in various organisms through the food chain,which can lead to various health problems to human beings, including teratogenicity,carcinogenicity and mutagenicity[3].Furthermore,paraquat could be rapidly adsorbed and strongly bonded to clay and organic matter in the soil,and it shows biologically inert and cannot be taken up by plant roots or other organisms[4].Thus,the extensive use of paraquat leads to severe contamination of soil and groundwater,which may pose adverse effects on the environmental ecosystem and human health.Therefore,it is of practical importance to find out an effective way to remove paraquat from polluted waters.

SnO2,usually comprised of tetragonal,hexagonal and orthorhombic crystal systems,has been widely used in gas sensor,semiconductor,spectralite and transparency electrode because of its low resistivity and high transmittance[5].SnO2as a n-type semiconductor with wide band gap(3.8 eV)is an excellent photocatalyst[6-8].However,due to its wide band gap, SnO2photocatalysis could only utilize UV light with λ<330 nm,which is less than about 3%of the sunlight spectrum,limiting its application by directly and fully utilizing the solar energy.Hence,great efforts have been made to enhance the visible light photocatalytic activity of SnO2,such as doping with metal/nonmetal elements to change the energy level and consequently broadening light responsive range to visible light region[9-12].

Sulfur is a multivalent element,and different doping technologies lead to different chemical states of sulfur in the crystal lattice and subsequently to exhibit different photocatalytic activities[13-14].As a facile, efficient and promising preparation method,solid-state reaction has been extensively applied in synthesis of high photocatalytic active nanomaterial.Herein,SnO2and S-doped SnO2nanoparticles were synthesized by a facile solid-state reaction approach at low temperature using sodium dodecyl benzene sulfonate(SDBS)as a template.Paraquat was chosen as the model pharmaceutical to evaluate the photocatalytic degradation activity of the as-synthesized nanomaterial under visible light irradiation.The relationships between the photocatalytic performances and the S-doping mechanism along with the structural characteristics of the resultant photocatalysts were investigated and discussed.

1 Experimental

1.1 Chem icals and materials

1.2 Preparation of S-doped SnO2

In a typical process,NaOH,SnCl4·5H2O and Na2S2O3·5H2O with a molar ratio of nNaOH∶nSnCl4·5H2O∶nNa2S2O3·5H2O=4∶0.9∶0.1 and SDBS with a mass fraction of 9%of total weight were ground with a mortar for 30 min at 20℃under the humidity of 75%.After stood for 4 h,the white viscous mixtures were heated at 120℃for 2 h in an oven.After cooling to room temperature,the mixtures were soaked in deionized water for 6 h with stirring The obtained solid specimen were washed with distilled water thoroughly until free from Cl-and SO42-and dried at 105℃,and then were finally heated to 600℃in a muffle furnace for 8 h with a heating rate of 2℃·min-1to obtain faint yellow photocatalysts of S-doped SnO2(S-SnO2(SDBS)). For comparison,white SnO2,white SnO2(SDBS)and faint yellow S-SnO2were also synthesized using identical condition in the absence of SDBS as well as Na2S2O3· 5H2O,Na2S2O3·5H2O and SDBS,separately.

1.3 Structural and m orphological characterizations

The XRD patterns were recorded by X′Pert Pro diffractometer using Cu Kα radiation(λ=0.154 06 nm, divergence slit fixed at 0.76 mm)at a scan speed of 0.02°·min-1from 5°to 80°,with a generator voltage of 40 kV,tube current of 40 mA,and a linear position sensitive detector.The surface morphologies of the synthesized photocatalysts were observed using a Field Emission Scanning Electron Microscopy(JEOL,JSM-6700F)with an accelerating voltage of 20 kV and a resolution of 1 nm.High resolution transmission electron microscopy(HRTEM)was observed with a JEOL-2100 operated at 200 kV.The FTIR spectra were investigated with a Spectrum 65 infrared spectrometer with a range of 4 000~400 cm-1and a spectral resolution of 1 cm-1.UV-Vis spectra were recorded on a Shimadzu UV-2550 spectrometer.The spectra were collected at 200~700 nm referenced to BaSO4.XPS was carried out on Thermo ESCALAB250 spectrometer using monochromated Al Kα(1 486.6 eV)source operated at 110 W.And the binding energies were referenced to the C1s line at 284.8 eV from adventitious carbon.The surface photovoltaic properties were performed on surface photovoltage spectrum(SPS) apparatus assembled by micro-/nanomaterials testing center of Hunan University.The surface photovoltage cell with a sandwich configuration(ITO/Sample/ITO) is shown in Fig.1.All tests were performed in indoor environment,and the data were obtained as the raw data.

Fig.1 Setup of surface photovoltage cell configuration

1.4 Photocatalytic activity test

The photocatalytic activity of as-prepared photocatalysts was evaluated by the photocatalytic degradation of paraquat in water under visible light irradiation.Photocatalytic degradation of paraquat by the as-prepared photocatalysts was performed in a 50 mL photochemical reactor XPA-Ⅶ(Nanjing Xujiang Elechtromechanical Factory,China).A 300 W metal halogen lamp assisted with Toshiba B-47 optical filter (λ>410 nm,transmittance>90%)was used as a visible light source.The reaction solution was kept at 25℃± 1℃by the water continuously circulated in the jacket surrounding the reactor and stirred with a magnetic stirrer throughout the experiment.Prior to illumination, a suspension of 20 mL 50 mg·L-1paraquat with 20 mg photocatalyst was stirred in the dark for 60 min to achieve the adsorption-desorption equilibrium.A 5 mL solution was taken at a given time interval and centrifuged for 5 min.The concentration of paraquat was determined by UV-Vis spectrophotometer at a wavelength of 257 nm.After detection,the detection solution was taken back into the quartz tube for next use.

2 Results and discussion

2.1 Structural and m orphological

characterization of photocatalysts

2.1.1 XRD analysis

Fig.2 XRD patterns of the samp les

Table1 Data of crystallite size and crystal p lane parameter for all sam p les

The wide-angle XRD patterns of the photocatalysts are displayed in Fig.2.All samples exhibit high intensity characteristic diffraction peaks of rutile SnO2,and no any other phases appear,suggesting rutile SnO2is the main phase in these samples.The peaks at 2θ values of 26.5°,33.9°,37.9°and 52.0° are attributed to the diffraction peaks of(110),(101), (200)and(211)crystal planes of rutile SnO2(PDF No. 411445),respectively.From the XRD patterns,SDBS shows an increase in intensity and a decrease in the peak width of diffraction peak,implying an increase in the crystallite size.Table 1 summarizes the crystallite sizes of all samples.As shown,the average crystallite sizes(d)of SnO2,SnO2(SDBS),S-SnO2and S-SnO2(SDBS)particles are 4.7,7.0,5.6,and 6.1 nm,respectively, as calculated by Bragg′s and Scherrer′s equation(D= 0.89λ/(βcosθ))from the peak at 2θ=26.5°,suggesting that the addition of SDBS is beneficial to the growth of the SnO2particles and increases in crystallinity. The diffraction peaks of(110)can be seen at 26.5° and 26.6°for SnO2and S-SnO2,respectively,implying that S with smaller ionic radius incorporates into the framework of SnO2by isomorphous substitution and subsequently leading to lattice distortion,the decrease of lattice distortion constant thus induces the increase of crystallite size.Similarly,the diffraction peaks of (110)can be observed at 26.4°and 26.7°for SnO2(SDBS)and S-SnO2(SDBS),respectively.This means that the addition of SDBS not only induces S into the lattice of SnO2,but also could regulate the crystallite size and interplanar spacing of SnO2by the guiding role of the molecular structure of SDBS,inferring that these samples may possess different photoelectric properties and photocatalytic activities,which could be corroborated by the results displayed in the following experiments.

2.1.2 SEM analysis

Fig.3 SEM images of samples

The SEM images of SnO2,S-SnO2,SnO2(SDBS)and S-SnO2(SDBS)are shown in Fig.3.The SnO2synthesized by solid-state reaction route shows the formation ofirregular spherical particle with a diameter distribution from 3.5~6.5 nm and an obvious agglomeration between the particles.The particulate size of S-SnO2is 4~7.5 nm,confirming that the reducing in particles agglomeration.It might be attributed to that Na2S2O3· 5H2O hinders the diffusion and transmission of SnCl4· 5H2O and NaOH.As expected,the particulate size range of SnO2(SDBS)and S-SnO2(SDBS)is 3.5~7.5 nm,and 3.0~8.0 nm,respectively,and the two samples show more regular sphere-like particles with smoother surfaces as compared to that of SDBS-free samples, suggesting that the addition of SDBS remarkably weakens the agglomeration of particles as its electrostatic effect and space location-obstruct effect. The TEM images of S-SnO2(SDBS)particles size are shown in Fig.4.Hollow micron-sized SnO2spheres with a diameter of ca.0.5~1 μm can be found(Fig. 4a),and these spheres are comprised of 5 nm SnO2nanoparticles(Fig.4b),agreeing with the crystallite size from the XRD data.The hollow micron-sized SnO2spheres are templated by surfactant SDBS with large hydrophilic group and long hydrophobic group, which favor the formation of spherical micelles in aqueous solutions by surfactant self-assembly,and then Sn4+cations interact with SDBS anions through Coulomb forces at the interface of the spherical micelles.Subsequently,the condensation of inorganic precursors of SnCl4is improved owing to the confined growth to form SnO2nanoparticles and aggregate around the spherical micelles of SDBS.Finally,the surfactant SDBS template can be removed by calcination to form hollow micron-sized SnO2spheres and hollow spherical fragments(nanoparticles).The corresponding selected-area electron diffraction (SAED)pattern(Fig.4c)indicates that the diffraction rings can be readily assigned to the polycrystalline nature of SnO2phase.The corresponding highresolution TEM(HRTEM)image(Fig.4d)shows that the interplanar distance of 0.33 nm is assigned to (110)plane of SnO2,which means that S incorporatesinto the lattice of SnO2leading to the shrink of the interplanar distance of SnO2compared with that of pure SnO2crystal(with the interplanar distance of (110)plane is 0.34 nm).The EDX elemental mapping performed on a typical hollow sphere demonstrates that the element content(atomic percentages,at%)of S within the structure is ca.3.4%,which also suggests that a small amount of S is embedded into the lattice of SnO2.

Fig.4 TEM images of S-SnO2(SDBS)

2.1.3 UV-Vis spectra

Fig.5 shows the UV-Vis spectra of SnO2,S-SnO2, SnO2(SDBS)and S-SnO2(SDBS).All samples exhibit an identical absorption in the UV region of the spectra, corresponding to the essential light absorption of SnO2crystal as the electron transition of SnO2from the valence band to the conduction band,and the UV-Vis spectra of the S-free and S-doped samples are rather similar.However,further observation reveals that the shape,slope and intensity of spectral line for the two samples are different.It may be one of evidences of the doping of S to the lattice of SnO2.Compared with SnO2,the absorption edge of S-SnO2displays a redshift,and the corresponding band gap decrease from 3.03 to 2.93 eV extrapolated by band gap estimation formula[15].As expected,S-SnO2(SDBS)also shows redshift as compared to SnO2(SDBS),and the band gap is 3.14 and 3.17 eV,respectively.It can be inferred that S-doping can improve the visible light absorption of the as-prepared photocatalysts due to the embedding of S into the SnO2lattice.Furthermore,the slower rate of diffusion and mass transfer in the solid-state reaction result in the crystal structure defects and imperfections,leading to the reduction of crystallinity and narrowing of the band gap of SnO2[16-18].

2.1.4 FTIR spectra

The FTIR spectra are shown in Fig.6.The absorbing peaks in the range of 620~640 cm-1can be assigned to the stretching vibration modes and bending vibration of Sn-O bond in SnO2[19-20].By comparing with the SnO2and SnO2(SDBS),it can be found that the samples of S-SnO2and S-SnO2(SDBS)exhibit absorbing peaks at 1 151 and 978 cm-1,and 1 130 and 931 cm-1,respectively,which can be attributed to the asymmetrical stretching vibration of O-S and bending vibration of Sn-O-S in S-doped SnO2[13,21].Moreover,the broad characteristic bands centered at 3 368,3 185,3 412 and 3 400 cm-1for SnO2,S-SnO2,SnO2(SDBS),and SSnO2(SDBS),respectively,can be assigned to the stretching vibration mode of H-O.It can be inferred from the difference of the peak position of H-O that the surficial polarities of resultant photocatalysts are different as the different degrees of association of H-O.The peaks at 1 630 cm-1are attributable to the bending vibration of H-O.Meanwhile,it is also found that the doping of S changes the peak position of bending vibration of H-O[16].

Fig.5 UV-Vis spectra of the samples

Fig.6 FTIR spectra of the samples

2.1.5 XPS analysis

The chemical compositions and chemical states of S-doped SnO2were characterized by XPS(Fig.7 and 8).The surface survey spectrum(Fig.7)shows the presence of the Sn4d,Sn4s,S2p,O1s,C1s,Sn3d and Sn3p peaks in the samples.The presence of C peak is due to the adventitious hydrocarbon from XPS instrument itself and the residual organic groups fromthe SDBS.The high-resolution XPS spectra of the Sn, O and S elements are provided in Fig.8.For S-SnO2(SDBS), two peaks for the Sn3d5/2and Sn3d3/2observed at 485.1 and 494.7 eV,respectively,are both assigned to Sn4+in rutile phase of SnO2[22].The spectrum of S2p shows a broad asymmetric curve at 168.0 eV,which can be deconvoluted into two peaks with binding energies at 167.6 eV for S/Sand 169.5 eV for S/S[22], respectively,with a S/S/S/Smolar ratio of 0.9.The binding energy peaks for O1s observed at 529.2 and 531.0 eV are originated from Sn-O-Sn bond in SnO2and the adsorbed oxygen,respectively.For S-SnO2, the peaks of Sn3d shift slightly to lower binding energies compared with that of S-SnO2(SDBS).The peaks positions of S2p are identical with S-SnO2(SDBS).Comparatively,S/S/S/Smolar ratio of S-SnO2is 1.43,indicating S/Sis significantly more than S/S,implying that the addition of SDBS remarkably influences the valence states of S,which means that these two samples may possess different photocatalytic performance.Combined with the XRD results,the characteristic diffraction peaks of SnO2for pure SnO2and S-doped SnO2does not exhibit any shifts except a change in the full width at half-maximum,implying no variation in the lattice parameters but lattice distortion appears as S/Sand S/Sare embedded into the lattice of SnO2to form Sn1-xSxO2[23].Since S is doped as S/S/ S/S,the state of mixing 3p of S with 2p of O should be clear,they should mainly contribute to the conduction band in S-doped SnO2.That is,the S-O-Sn bond on the nanomaterial surface must be presented in FTIR spectra.Usually,if the S is doped as S2-,such kind of orbital mixing should occur,but not for the S doped as S/S/S/Soxidation state.These are consistent with the results in Fig.3 and Fig.4.Therefore,the origin of the slight extension of the visible light absorption after S doping is undoubted.It might be due to the nanoparticle size,defect effect,and mixing of p orbitals of S/S/S/Swith O2-.

Fig.7 Surface survey XPS spectra of S-doped SnO2

Fig.8 High-resolution XPS spectra of O1s,Sn3d and S2p for S-SnO2and S-SnO2(SDBS)

2.2 Photocatalytic degradation of paraquat

The photocatalytic degradation of a typical herbicide,paraquat under visible light irradiation is shown in Fig.9.These samples show obviously different adsorption capabilities towards paraquat(c0=50 mg·L-1) due to the different surface states,and the adsorption equilibrium is achieved within 60 min for all samples. No noticeable changes of paraquat concentration could be observed within 120 min under visible light irradiation without the addition of photocatalyst, indicating that only photolysis could not efficiently decompose the paraquat.As expected,the S-doped SnO2exhibits high photocatalytic activity,and it follows an order of SnO2(6.5%)

Fig.9 Photodegradation of paraquat under visible light irradiation

2.3 Photoeletrochem ical characterization

Fig.10 shows the surface photovoltaic spectra (SPS)of sampleswithapplied potential bias of+0.5 V. Among all investigated samples,the surface photovoltage response of these nanopowder is positively correlated to the UV absorption intensity and range,that is,the surface photovoltage follows the order of S-SnO2(SDBS)(0.006 36 mV)>SnO2(SDBS)(0.005 01 mV)>S-SnO2(0.002 22 mV)>SnO2(0.000 46 mV). Comparatively,the surface photovoltage of S-SnO2(SDBS)is 13.8 times higher than that of SnO2under the same condition,suggesting that S-doped SnO2have higher efficiency to transport the photogenerated electrons than SnO2.From Fig.8,the surface photovoltage response of the samples can also be observed at 420~600 nm with a weak peak,attributing to the existence of a large amount of surfaces states and Dember effect.The surface state could change the configuration of nanoparticle′s surface atoms,electron spin and electronic transition.Based on EFISPS principle,the surface state is sensitive towards the external electric field,an external electric field enhances the transition probability of surface state to generate surface photovoltage response signals in the long wavelength[25].The stronger of the SPS signal is,the higher the efficiency of photoinduced charge separation.This is consistent with the results of visible-light degradation.Simultaneously,surface oxygen vacancies and defects enhance the separation of photogenerated charges at the interface,resulting in the higher photodegradation efficiency of paraquat.

Fig.10 Electrical field induced surface photovoltage spectra in the samples

From the results above,it can be deduced that the surficial states of photocatalyst have a significant effect on the photocatalytic activity.As for S-SnO2(SDBS), the S element is successfully incorporated into the lattice of SnO2with S/S/S/Sby substituting Sn4+, rather than embedded into the interstice of SnO2lattice,thereby leading to lattice distortion.The S3p level could mix with O2p which results in the narrowing of the band gap and enhancing the photocatalytic activity.Moreover,the formation of the localized midgap state above the top of the valence band for SnO2might be responsible for increasing thephotoactivity of SnO2in the visible region[26].The average size of S-SnO2(SDBS)is lower than 6 nm as the doping of S,leading to the enhanced absorption of light because of the quantum size effect and subsequently enhancing the amount of photo-induced carrier. Additionally,a large amount of hydroxyl groups in SSnO2(SDBS)are beneficial to generating highly reactive ·OH,thus accelerating the degradation of paraquat.It should also be noted that the ratio of S/Sin S-SnO2(SDBS)is obviously more than that of S-SnO2,which also enhances the degradation of paraquat because S/Shas stronger oxidation capacity than S/S.

3 Conclusions

In this work,S-doped SnO2nanoparticles with superior visible light photocatalytic activity was fabricated via a facile solid state synthesis approach at low temperature using sodium dodecyl benzene sulfonate(SDBS)as template.The S element is successfully incorporated into the lattice of SnO2with S/S/S/Sinstead of embedding into the interstice of SnO2lattice.S-doped SnO2could significantly improve visible light utilization property,thus resulting in narrowed band gap.SDBS has a significant regulating effect on the surficial structure of photocatalysts.The photocatalytic activity shows significant correlation with particle size,particle size distribution and the ratio of S/S/S/S.S-doped SnO2exhibits higher photocatalytic activity,and it follows an order of SnO2

Acknow ledgements:This work was supported by the Education Quality Promotion Foundation of Department of Education,Guizhou Province,China(No.[2011]278-01),Guizhou Province Characteristic Leading Academic Discip line Project in Material Physics and Chem istry(No.[2011]208),Characteristic Key Laboratory Construction Fund of Guizhou Province(No. [2012]014),and Science and Technology Innovation Talent Team Foundation of Guizhou Province,China(No.[2013]4029).

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Sulfur Doped Tin Oxide Nanoparticles:Solid State Synthesis and Performance for Visible-Light Driven Photocatalytic Degradation of Paraquat

HE Zhong-Bing1,2LIU Shao-You*,1,3YANG Hong-Yun1MIN Zong-Yi2NIE Xin1
(1College of Chemistry and Materials Engineering,Kaili University,Kaili,Guizhou 556011,China)
(2College of Envirnomental Science and Engineering,Hunan University,Changsha 410082,China)
(3School of Envirnomental Studies,Guangxi University,Nanning 530004,China)

Sulfur doped tin oxide(S-SnO2)nanoparticles with high visible light-driven activity was synthesized by a facile solid state synthesis approach at low temperature using sodium dodecyl benzene sulfonate(SDBS)as a template.The samples were characterized by XRD,XPS,SEM,UV-Vis,HR-TEM,and FTIR.The doping mechanism and photocatalytic degradation of paraquat under visible light irradiation were investigated.The results show that the SDBS has a significant regulating effect on the surficial structure for both SnO2and S-SnO2prepared by solid state synthesis.The S element is successfully incorporated into the lattice of SnO2with S/Sand S/Srather than embeds into the interstice of SnO2lattice.S-doping enhances the photocatalytic activity of SnO2due to the presence of a large number of hydroxyls on the surface and S/Sin the lattice of SnO2benefiting the light absorption and effective charge separation,and it follows an order of SnO2

S-doped;SnO2;solid state synthesis;photocatalytic degradation;paraquat

O643.36

A

1001-4861(2015)04-0649-10

10.11862/CJIC.2015.117

2014-09-01。收修改稿日期:2015-02-08。

貴州省科技創(chuàng)新人才團隊建設基金項目(黔科人字[2013]4029);貴州省材料物理與化學特色重點學科建設基金項目(黔教高發(fā)[2011]208);貴州省教育廳特色重點實驗室建設基金項目(黔教高發(fā)[2012]196);貴州省教育廳市州地普通本科高校教育質量提升科研項目(黔教高發(fā)[2011]278-01)資助。

*通訊聯(lián)系人。E-mail:lsy651204@163.com

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