• <tr id="yyy80"></tr>
  • <sup id="yyy80"></sup>
  • <tfoot id="yyy80"><noscript id="yyy80"></noscript></tfoot>
  • 99热精品在线国产_美女午夜性视频免费_国产精品国产高清国产av_av欧美777_自拍偷自拍亚洲精品老妇_亚洲熟女精品中文字幕_www日本黄色视频网_国产精品野战在线观看 ?

    Preparation of Bi2WO6and Its Ultra-Deep Oxidative Desulfurization Performance in Ionic Liquids

    2017-05-09 15:37:40XingPengfeiZhaoRongxiangLiXiupingGaoXiaohan
    中國(guó)煉油與石油化工 2017年1期

    Xing Pengfei; Zhao Rongxiang; Li Xiuping; Gao Xiaohan

    ( College of Chemistry, Chemical Engineering and Environmental Engineering, Liaoning Shihua University, Fushun 113001 )

    Preparation of Bi2WO6and Its Ultra-Deep Oxidative Desulfurization Performance in Ionic Liquids

    Xing Pengfei; Zhao Rongxiang; Li Xiuping; Gao Xiaohan

    ( College of Chemistry, Chemical Engineering and Environmental Engineering, Liaoning Shihua University, Fushun 113001 )

    The micro-spheric Bi2WO6was synthesized by a simple one-step hydrothermal method. Bi2WO6crystals were characterized using XRD, SEМ, EDS and BET techniques. Bi2WO6, H2O2and [HMIM][BF4] served as catalyst, oxidant and extracting agent in the oxidative desulfurization system (ODS), respectively. The infuence of extraction agent type, oxidant usage, catalyst dosage, temperature, sulfur compound type and other factors on the oxidative desulfurization was studied in the present work. The experimental results demonstrate that Bi2WO6possesses high activity for desulfurization of dibenzothiophene (DBT) and benzothiophene (BT). The desulfurization rate of DBT and BT in model oil could reach 98.1% in 80 minutes and 96.2% in 120 min at 70oC, respectively. Мoreover, the desulfurization performance of catalyst for DBT hardly changed after being recycled for 10 times.

    Bi2WO6; catalyst; oxidative desulfurization; [HMIM][BF4]; dibenzothiophene

    1 Introduction

    SOxemission from fuel oil pollutes the environment and endangers human health[1-2]. Therefore, many countries in the world have formulated stringent environmental regulations to limit sulfur content in the fuel (S content <10 μg/g)[3]. Traditional hydrodesulfurization (HDS) can only be used to remove some of the sulfur compounds in fuel, such as thiols, sulfides, disulfides, etc. However, these sulfur compounds, such as DBT and its derivatives, can hardly be removed from fuel. For removing these sulfur compounds, some operating conditions (high temperature, high pressure and high hydrogen consumption) and large capital cost are needed[4-5]for implementing the HDS process. Thus, non-hydrodesulfurization technologies have been developed[6-12], such as oxidative desulfurization, biological desulfurization, absorptive desulfurization, extractive desulfurization, etc. Among these techniques, catalytic oxidative desulfurization is the most attractive technologies due to its mild reaction conditions and high sulfur removal rate.

    In the ODS process, sulfur compounds are oxidized into the corresponding sulfoxide and sulfone, which can be readily removed by extraction methods[13]. A lot of oxidation agents have been used, such as oil-soluble oxidants[14], H2O2[15], and solid oxidizing agents[16]. Among these oxidants, H2O2is the most attractive because the by-product is H2O, so it does not pose a new threat of pollutant in the reaction system. Thus, H2O2is considered as a green oxidant.

    The catalyst also play an important role in ODS process. Sodium tungstate as an efficient catalyst is used in the oxidative desulfurization process. For example, Liu Dan, et al.[17-18]reported that the desulfurization rate could reach up to 100% using sodium tungstate as catalyst in the ODS process. Collins, et al.[19]indicated that the desulfurization rate can reach 96% using sodium tungstate as catalyst in the presence of H2O2. However, it is difficult to recycle and reuse the catalyst due to the fact that sodium tungstate can easily dissolve in water.

    In this study, Bi2WO6was synthesized by the simple onestep hydrothermal method. The oxidative desulfurization process was studied using Bi2WO6as the catalyst, H2O2as the oxidant and [HMIM][BF4] as extracting agent.Bi2WO6was highly effcient on the removal of DBT and could be easily separated for the recycling mixture under mild conditions. In addition, the reaction mechanism of the catalyst was discussed in detail.

    2 Experimental

    2.1 Chemical reagents

    30% hydrogen peroxide (H2O2, A.R.), bismuth (III) nitrate pentahydrate (Bi(NO3)3·5H2O, A.R.) andn-octane (A.R.), were purchased from the Sinopharm Shanghai Chemical Reagent Co. Ltd. Dibenzothiophene (DBT, 98%), benzothiophene (BT, 99%), and thiophene (TH, 99.8%) were purchased from the Aladdin Industrial Corporation. Sodium tungstate (Na2WO4·2H2O, 99%) was purchased from the No. 2 Chemical Reagent Factory. 1-n-Hexyl-3-methylimidazolium tetrafluoroborate ([HMIM][BF4]) and 1-ethyl-3-methylimidazolium ethylsulfate ([EMIM] [EtSO4]) were purchased from the Shanghai Chengjie Chemical Co. Ltd. All reagents were directly used without further purifcation.

    2.2 Characterization

    X-Ray powder diffraction (XRD) analysis of the samples was carried out at room temperature on a BRUKER D8 ADVANCE X-ray powder diffractometer (Bruker Corp.) with Cu-Kα radiation (λ=0.154 06 nm) and a scanning speed of 10(°)/min, with the accelerating voltage and emission current equating to 40 kV and 40 mA, respectively. Scanning electron microscopy (SEМ) and energy dispersive spectroscopy (EDS) were performed on a FEI Sirion200 scanning electron microscope (USA), using a scanning voltage of 5.00 kV for studying the morphology and elements of samples. The N2adsorptiondesorption measurement was tested using a TriStar II 3020 surface area and porosity analyzer (Micromeritics Instrument Corp.). The infrared spectroscopic analysis was implemented on a WQF-520 Fourier-transform infrared spectrometer (Beifen Ruili Analytical Instrument Company).

    2.3 Preparation of the catalysts

    The micro-spheric Bi2WO6was synthesized by the onestep hydrothermal method. Bi(NO3)3·5H2O (4.85 g) was dissolved in 40 mL of water prior to staying overnight to get a transparent solution (labeled as solution A); Na2WO4·2H2O (1.645 g) was dissolved in 40 mL of water to get a transparent solution (labeled as solution B). The solution B was added into the solution A under stirring, with the transparent mixture solution entering into reaction for 15 minutes. The transparent solution was placed into an 80-mL Tefon-lined autoclave at 160oC for 24 h. Then, the suspension solution was separated by centrifugation, washed with water for three times and dried in an oven at 100oC for 24 h.

    2.4 Oxidative desulfurization procedure of model fuelThe model oil was obtained by dissolving 1.437 g of DBT in 500 mL ofn-octane, with its initial sulfur content reaching 500 μg/g. The catalyst, model oil, ionic liquids and H2O2(30%) were successively added into an 100-mL Erlenmeyer flask equipped with a condenser. Then the Erlenmeyer fask was heated in a water bath provided with a magnetic stirrer. After a specifed time, the reaction system was naturally cooled down to room temperature before separation into two layers. The sulfur content in the upper oil phase was tested with a WK-2D micro computer coulomb comprehensive analyzer.

    3 Results and Discussion

    3.1 Phase analysis of samples

    Figure 1 The XRD patterns of the samples (1)—The fresh Bi2WO6sample; (2)—Used Bi2WO6sample after 10 cycles

    The crystal phase and structure of Bi2WO6were analyzed by XRD technique. The results are shown in Figure 1. According to XRD patterns, the peaks at 28.3°, 32.8°, 47.2°, 55.8°, 58.5° and 68.7° are attributed to the plane of (113), (024), (220), (313), (226) and (400) of Bi2WO6, which are consistent with the standard crystal card ofBi2WO6(JCPDS No. 39-0256). The Bi2WO6sample exhibits higher intensity and narrower diffraction peaks in Figure 1, the results indicate that the crystallinity and purity of Bi2WO6are high. The pattern peaks of the used and the fresh catalyst samples hardly change, which demonstrates that the catalyst is preeminently stabilized during the ODS reaction.

    3.2 The morphology and energy dispersive spectroscopy

    Figure 2 shows SEM pictures of the Bi2WO6sample. It can be seen that micro-sphere Bi2WO6is assembled with hundreds of nanosheets. The diameter of microspheres is about 3—5 μm. The enlarged image of the sample is shown in Figure 2 (b), where the micro-spheric Bi2WO6is composed of thin sheets according to a certain rule. It can be observed that the as-prepared samples only contain O, W and Bi elements, and no other impurity peaks appear in Figure 3, which demonstrates that Bi2WO6samples exhibit a high purity.

    Figure 2 SEM pictures of the Bi2WO6samples

    3.3 N2adsorption-desorption analysis

    In order to study the specifc surface area and pore size distribution, N2adsorption-desorption analysis was carried out for the as-synthesized Bi2WO6. The isotherms can be observed in Figure 4 at a relative pressure (P/P0) of 0.5—1.0 with a hysteresis loop, showing the characteristics of the IV types of curves. The pore size distribution curve in the illustration confirms that the structure of the microspheric Bi2WO6is comprised of 2—50 nm mesopores, with the pore size being centrally located at about 18.131 3 nm. There is a large mesopore sized up to about 50 nm, which is formed due to overlap between fower-like Bi2WO6, and smaller pores are formed due to crossed arrangement between nanosheets. The specific surface area and pore volume of the sample are 28.554 0 m2/g and 0.127 806 cm3/g, respectively.

    Figure 3 EDS pictures of the Bi2WO6sample

    Figure 4 N2adsorption-desorption and pore size distribution of the fower-like Bi2WO6

    3.4 Optimizing the reaction conditions of model fuel

    3.4.1 Influence of different desulfurization systems on removal rate of DBT

    Four different oxidation desulfurization systems, [EMIM][EtSO4]/H2O2, [EМIМ][EtSO4]/ H2O2/Bi2WO6, [HMIM][BF4]/H2O2and [HMIM][BF4]/H2O2/Bi2WO6were chosen for studying their effect on removal of DBTunder same conditions. Experimental results are shown in Table 1. The desulfurization rate of DBT in model oil only reached 10% in the system of [EMIM]EtSO4/ H2O2; however, the desulfurization rate increased to 24.2% with the addition of Bi2WO6in [EMIM][EtSO4]/ H2O2. When [HМIМ][BF4]/H2O2was used as a system to remove DBT in model oil, the desulfurization rate of DBT increased to 46.1%. In the system of [HМIМ] [BF4]/H2O2/Bi2WO6, the desulfurization rate of DBT increased sharply to 98.7%. These results showed that the type of ionic liquid and Bi2WO6had important influence on the desulfurization efficiency. Compared with two kinds of ionic liquids, [HМIМ][BF4] exhibited higher desulfurization activity due to its stronger extraction ability[20]. However, the desulfurization rate of the system still significantly increased by the addition of Bi2WO6. Obviously, the desulfurization system containing Bi2WO6, [HМIМ][BF4] and H2O2was evidently superior to other desulfurization systems studied in the present work.

    Table 1 Infuence of different desulfurization system on sulfur removal of DBT

    3.4.2 Investigation of conditions adopted in the ODS process

    Bi2WO6was used as the catalyst, H2O2as the oxidation agent, and [HМIМ][BF4] as the extraction agent in the oxidative desulfurization process. The reaction conditions were studied for obtaining the optimal desulfurization effect, as shown in Figure 5. The desulfurization rate could reach 98.7% under the optimal conditions (V(DBT, oil)=5 mL,w(DBT)=500 μg/g,T=70oC,V([HMIM] [BF4])=1.0 mL,m(Bi2WO6)=0.04 g,n(O)/n(S)=15,t=180 min). The desulfurization rate was enhanced by increasing the amount of Bi2WO6,n(O)/n(S), [HМIМ]BF4and raising the reaction temperature in the ODS process. However, excessive Bi2WO6,n(O)/n(S) and [HMIM] BF4for 5 mL of model oil could no longer accelerate the desulfurization rate. Besides, higher reaction temperature would lead to the decomposition of H2O2into H2O.

    3.4.3 Influence of different sulfur compounds on sulfur removal rate

    The catalyst for different sulfur compounds in model oil has different oxidation activity. The experimental data are shown in Figure 6, with the sulfur removal rate decreasing in the following order: DBT > BT > TH under the same reaction conditions. The desulfurization rate of DBT, BT and TH reached 98.7% in 80 min, 97.2% in 120 min and 51.3% in 140 min, respectively. The desulfurization rate relied on the electron density of the sulfur atoms contained in organic sulfides. Generally, lower electron density in sulfur atom has a lower desulfurization rate. For DBT, BT and TH, the electron density of the sulfur atom is 5.785, 5.739 and 5.696[21], respectively. Hence, the activity was related with the infuence of the electron density.

    3.4.4 The recycling performance of the catalyst

    The performance on recovery of the catalyst activity was researched during the ODS reaction. After each desulfurization reaction, the catalyst was separated by centrifugation. The separated catalyst was dried in a vacuum oven at 100oC. Subsequently, the recovered catalyst, fresh model oil, ionic liquids and H2O2were placed in the Erlenmeyer fask under the same reaction conditions. The experimental results are shown in Figure 7. It was found that the Bi2WO6after being recycled for ten times did not show a decrease in its activity. Thereby, the XRD pattern of recycled Bi2WO6was determined. It can be observed that the diffraction peaks of the used Bi2WO6were consistent with those of the fresh catalyst shown in Figure 2. The results demonstrate that the catalyst is quite stable during the ODS reaction.

    Figure 5 The conditions of oxidative desulfurization(a)Infuence of the amount of H2O2on the desulfurization rate (V(DBT, oil)=5 mL,w(DBT)=500 μg/g,V([HMIM][BF4])=1.0 mL,T=70oC,m(Bi2WO6)=0.02 g,t=180 min); (b) Infuence of catalyst amount on the desulfurization rate (V(DBT, oil)=5 mL,w(DBT)=500 μg/g,V([HMIM][BF4])=1.0 mL,T=70oC,n(O)/n(S)=15,t=180 min); (c) Infuence of reaction temperature on the desulfurization rate (V(DBT, oil)=5 mL,w(DBT)=500 μg/g,V([HMIM][BF4])=1.0 mL,m(Bi2WO6)=0.04 g,n(O)/n(S)=15,t=180 min); (d) Infuence of the IL amount on the desulfurization rate (V(DBT, oil)=5 mL,w(DBT)=500 μg/g,T=70oC,m(Bi2WO6)=0.04 g,n(O)/n(S)=15,t=180 min)

    Figure 6 Sulfur removal activity of the reaction system for different sulfur compounds (V(Oil)=5 mL,w(DBT)=500 μg/g,w(BT)=500 μg/g,w(TH)=500 μg/g,T=70oC,m(Bi2WO6)=0.04 g,n(O)/n(S)=15,V([HMIM][BF4])=1.0 mL,t=180 min)■—DBT;●—BT;▲—TH

    Figure 7 The recycling performance of the catalyst (V(DBT, oil)=5 mL,w(DBT)=500 μg/g,T=70oC,m(Bi2WO6)=0.04 g,n(O)/n(S)=15,V([HMIM][BF4])=1.0 mL,t=180 min.)

    In order to ascertain the type of oxidation products derived from these sulfur compounds, the reverse extraction experiment was implemented using carbon tetrachloride as the solvent. Then, the carbon tetrachloride phase was removed by rotary evaporation and a white solid was obtained. The structure of the gained white sedimentwas measured by FT-IR spectroscopy, with the results shown in Figure 8. In comparison with the adsorption peaks for DBT, there were absorption peaks for sulfone at 128 6 cm-1and 116 8 cm-1[22], and also absorption peak for sulfoxide at 104 5 cm-1[22], demonstrating that DBT in model oil was oxidized to DBTO and DBTO2when Bi2WO6was employed as the catalyst.

    Figure 8 FT-IR spectra of DBT (A) and its oxidation products (B)

    3.4.5 Reaction mechanism of oxidative desulfurization

    Recently, sodium tungstate was chosen as the catalyst in the ODS process. The activity of the catalyst mainly derives from peroxotungstate, which is obtained through oxidation of sodium tungstate by H2O2. Мa(chǎn)jid Vafaeezadeh, et al.[23]synthesized silver tungstate, which served as the catalyst for the photoxidative cleavage of cyclohexene to adipic acid. Research shows that silver tungstate can form peroxotungstate under the action of hydrogen peroxide. The peroxotungstate plays an important role in the formation of oxidation products. Sivasankara Rao Ede, et al.[24]found that SnWO4can be oxidized by H2O2to form Sn(WO(O2)2(OH)2). The Sn(WO(O2)2(OH)2) plays a crucial role for the oxidation of butanol to butanoic acid. Inspired by these facts, we believe that bismuth tungstate can also be oxidized by hydrogen peroxide into corresponding peroxide.

    The oxidative desulfurization process of sulfur compounds contains two steps. One is the extract and other is the oxidation reaction[25]. Firstly, the DBT in model oil is extracted into IL phase. DBT is oxidized by Bi[WO(O2)2(OH)2] into the corresponding sulfoxide[24]. Then the oxidation reaction of sulfur compounds could lead to the reduction of the concentration of DBT in the ionic liquid to further realize the extraction process and oxide formation. Therefore, the ultra-deep removal of sulfur compounds could be attained. The mechanism of catalytic oxidation and extraction of products derived from for DBT is described in Figure 9.

    Figure 9 Extraction and catalytic oxidation course of deep oxidative desulfurization process

    4 Conclusions

    In conclusion, the micro-spheric Bi2WO6was synthesized by the simple one-step hydrothermal method. The Bi2WO6was used as the catalyst, H2O2as the oxidant and [HMIM]BF4as the extraction agent for the ultradeep desulfurization of model oil. Under the optimal experimental conditions (V(Oil)=5 mL,w(DBT)=500 μg/g,T=70oC,m(Bi2WO6)=0.04 g,n(O)/n(S)=15, V([HМIМ] [BF4])=1.0 mL), the sulfur removal of DBT and BT could reach 98.7% in 80 min and 97.2% in 120 min. The results demonstrate that the oxidative desulfurization process is highly effective for treating DBT and BT. The catalytic activity did not decline after 10 times of catalyst recycles, which demonstrated that the catalyst was stable because it did not lose its activity in the heterogeneous ODS reaction.

    Acknowledgements:The authors also acknowledge the financial support of the Natural Science Foundation of China (Project No. 21003069) and the Doctoral Fund of Liaoning Province (201501105).

    [1] Zhu W, Wang C, Li H, et al. One-pot extraction combined with metal-free photochemical aerobic oxidative desulfurization in deep eutectic solvent[J]. Green Chemistry, 2015, 17(4): 2464-2472

    [2] Li F, Liu R, Wen J, et al. Desulfurization of dibenzothiophene by chemical oxidation and solvent extraction with Me3NCH2C6H5Cl· 2ZnCl2ionic liquid[J]. Green Chemistry, 2009, 11(6): 883-888

    [3] E?er J, Wasserscheid P, Jess A. Deep desulfurization of oil refinery streams by extraction with ionic liquids[J]. Green Chemistry, 2004, 6(7): 316-322

    [4] Li H Y, Gao J B, Jiang Z X. Ultra-deep desulfurization of diesel by selective oxidation with [C18H37N(CH3)3]4[H2NaPW10O36] catalyst assembled in emulsion droplets[J]. J Catal, 2006, 239(2): 369

    [5] Wang Z, Chen S L, Pei J, et al. Insight into the intraparticle diffusion of residue oil components in catalysts during hydrodesulfurization reaction[J]. AIChE Journal, 2014, 60(9): 3267-3275

    [6] Campos-Мa(chǎn)rtin J М, Capel-Sanchez М C, Fierro J L G. Highly efficient deep desulfurization of fuels by chemical oxidation[J]. Green Chemistry, 2004, 6(11): 557-562

    [7] Li C, Jiang Z, Gao J, et al. Ultra-deep desulfurization of diesel: Oxidation with a recoverable catalyst assembled in emulsion[J]. Chemistry-A European Journal, 2004, 10(9): 2277-2280

    [8] Hernández‐Мa(chǎn)ldonado A J, Yang R T. Desulfurization of transportation fuels by adsorption[J]. Catalysis Reviews, 2004, 46(2): 111-150

    [9] Babich I V, Мoulijn J A. Science and technology of novel processes for deep desulfurization of oil refnery streams: A review[J]. Fuel, 2003, 82(6): 607-631

    [10] Song C. An overview of new approaches to deep desulfurization for ultra-clean gasoline, diesel fuel and jet fuel[J]. Catalysis Today, 2003, 86(1): 211-263

    [11] Ito E, Van Veen J A R. On novel processes for removing sulphur from refinery streams[J]. Catalysis Today, 2006, 116(4): 446-460

    [12] Rang H, Kann J, Oja V. Advances in desulfurization research of liquid fuel[J]. Oil Shale, 2006, 23(2): 164-176

    [13] Anisimov A V, Fedorova E V, Lesnugin A Z, et al. Vanadium peroxocomplexes as oxidation catalysts of sulfur organic compounds by hydrogen peroxide in biphase systems[J]. Catalysis Today, 2003, 78(1): 319-325

    [14] Venkateshwar Rao T, Sain B, Kafola S, et al. Oxidative desulfurization of HDS diesel using the aldehyde/ molecular oxygen oxidation system[J]. Energy & Fuels, 2007, 21(6): 3420-3424

    [15] Jiang X, Li H, Zhu W, et al. Deep desulfurization of fuels catalyzed by surfactant-type decatungstates using H2O2as oxidant[J]. Fuel, 2009, 88(3): 431-436

    [16] De Filippis P, Scarsella М. Functionalized hexagonal mesoporous silica as an oxidizing agent for the oxidative desulfurization of organosulfur compounds[J]. Industrial & Engineering Chemistry Research, 2008, 47(3): 973-975

    [17] Liu D, Gui J, Ding J, et al. Oxidation of dibenzothiophene catalyzed by Na2WO4in a halogen-free ionic liquid[J]. Reaction Kinetics, Мechanisms and Catalysis, 2011, 104(1): 111-123

    [18] Liu D, Gui J, Liu D, et al. Deep oxidative desulfurization of real diesel catalyzed by Na2WO4in ionic liquid[J]. Energy Sources, Part A: Recovery, Utilization, and Environmental Effects, 2013, 35(1): 1-8

    [19] Rakhmanov E V, Anisimov A V, Tarakanova A V, et al. Oxidative desulfurization of catalytically cracked gasoline with hydrogen peroxide[J]. Petroleum Chemistry, 2013, 53(3): 201-204

    [20] Lu L, Cheng S, Gao J, et al. Deep oxidative desulfurization of fuels catalyzed by ionic liquid in the presence of H2O2[J]. Energy & Fuels, 2007, 21(1): 383-384

    [21] Zhang J, Zhu W, Li H, et al. Deep oxidative desulfurization of fuels by Fenton-like reagent in ionic liquids[J]. Green Chemistry, 2009, 11(11): 1801-1807

    [22] Zhang H, Gao J, Мeng H, et al. Removal of thiophenic sulfurs using an extractive oxidative desulfurization process with three new phosphotungstate catalysts[J]. Industrial & Engineering Chemistry Research, 2012, 51(19): 6658-6665

    [23] Vafaeezadeh М, Hashemi М М. One pot oxidative cleavage of cyclohexene to adipic acid using silver tungstate nanorods in a Br?nsted acidic ionic liquid[J]. RSC Advances, 2015, 5(40): 31298-31302

    [24] Ede S R, Kundu S. Мicrowave synthesis of SnWO4nanoassemblies on DNA scaffold: A novel material for high performance supercapacitor and as catalyst for butanol oxidation[J]. ACS Sustainable Chemistry & Engineering, 2015, 3(9): 2321-2336

    [25] Zhao D, Wang J, Zhou E. Oxidative desulfurization of diesel fuel using a Br?nsted acid room temperature ionic liquid in the presence of H2O2[J]. Green Chemistry, 2007, 9(11): 1219-1222

    Received date: 2016-08-29; Accepted date: 2016-10-19.

    Dr. Zhao Rongxiang, E-mail: zylhzrx@126.com.

    日韩亚洲欧美综合| 观看美女的网站| 国产精品电影一区二区三区| 国产精品国产高清国产av| 婷婷丁香在线五月| 精品人妻偷拍中文字幕| 蜜桃亚洲精品一区二区三区| 他把我摸到了高潮在线观看| 欧美高清成人免费视频www| 欧美成人性av电影在线观看| 少妇高潮的动态图| 别揉我奶头~嗯~啊~动态视频| 亚洲av美国av| 久久久久国产精品人妻aⅴ院| x7x7x7水蜜桃| 午夜福利欧美成人| 欧美另类亚洲清纯唯美| 国产蜜桃级精品一区二区三区| 成年人黄色毛片网站| 伊人久久精品亚洲午夜| 国产精品亚洲一级av第二区| 熟女人妻精品中文字幕| 88av欧美| 不卡一级毛片| 国产精品电影一区二区三区| 性色avwww在线观看| 国产一区在线观看成人免费| 亚洲在线观看片| 亚洲五月婷婷丁香| 五月伊人婷婷丁香| 天堂av国产一区二区熟女人妻| 久久久精品欧美日韩精品| 欧美三级亚洲精品| 精品人妻一区二区三区麻豆 | 国产私拍福利视频在线观看| 男女那种视频在线观看| 岛国在线免费视频观看| 欧美日本亚洲视频在线播放| 免费一级毛片在线播放高清视频| 一边摸一边抽搐一进一小说| 国产一区在线观看成人免费| 三级男女做爰猛烈吃奶摸视频| 欧洲精品卡2卡3卡4卡5卡区| 欧美在线一区亚洲| 午夜免费观看网址| 午夜免费男女啪啪视频观看 | 免费观看精品视频网站| 日韩亚洲欧美综合| 亚洲av成人av| 精品不卡国产一区二区三区| 天堂影院成人在线观看| 亚洲精品影视一区二区三区av| 久久精品国产亚洲av香蕉五月| 又紧又爽又黄一区二区| 久久国产精品人妻蜜桃| 久久午夜亚洲精品久久| 在线观看美女被高潮喷水网站 | 黄色成人免费大全| av片东京热男人的天堂| 天美传媒精品一区二区| 人人妻,人人澡人人爽秒播| netflix在线观看网站| 色av中文字幕| 少妇裸体淫交视频免费看高清| av欧美777| 免费av不卡在线播放| 国产在线精品亚洲第一网站| 亚洲国产色片| 舔av片在线| 男女午夜视频在线观看| 韩国av一区二区三区四区| 特大巨黑吊av在线直播| 亚洲欧美日韩高清专用| 亚洲黑人精品在线| 午夜福利免费观看在线| 欧美在线黄色| 国内精品美女久久久久久| 中文在线观看免费www的网站| 欧美xxxx黑人xx丫x性爽| 亚洲性夜色夜夜综合| 亚洲熟妇熟女久久| 波多野结衣高清无吗| 亚洲av二区三区四区| 成人精品一区二区免费| tocl精华| 亚洲最大成人中文| 欧美乱妇无乱码| 国产精品影院久久| h日本视频在线播放| 高潮久久久久久久久久久不卡| 免费人成视频x8x8入口观看| 人人妻,人人澡人人爽秒播| 91在线观看av| 免费观看的影片在线观看| 色综合站精品国产| 成人特级黄色片久久久久久久| 99精品在免费线老司机午夜| 一级黄片播放器| 欧美黄色片欧美黄色片| 好男人电影高清在线观看| 午夜久久久久精精品| 青草久久国产| 国产欧美日韩精品亚洲av| 国产老妇女一区| 精品一区二区三区av网在线观看| 午夜精品久久久久久毛片777| 国产伦精品一区二区三区视频9 | 色视频www国产| 国产成年人精品一区二区| 每晚都被弄得嗷嗷叫到高潮| 可以在线观看毛片的网站| 一级黄片播放器| 舔av片在线| 亚洲精品成人久久久久久| 中文亚洲av片在线观看爽| 制服人妻中文乱码| 国产麻豆成人av免费视频| 国产一区二区激情短视频| 国产三级在线视频| 日韩国内少妇激情av| 欧美成人免费av一区二区三区| 麻豆国产av国片精品| 久久久久久久久久黄片| 无遮挡黄片免费观看| 婷婷精品国产亚洲av| 亚洲午夜理论影院| 一卡2卡三卡四卡精品乱码亚洲| 成人性生交大片免费视频hd| 午夜福利在线观看吧| 舔av片在线| АⅤ资源中文在线天堂| 我的老师免费观看完整版| 手机成人av网站| 久久精品国产综合久久久| www.熟女人妻精品国产| 久久久国产成人精品二区| 69av精品久久久久久| 日本熟妇午夜| 可以在线观看毛片的网站| 久久久色成人| 女人十人毛片免费观看3o分钟| 长腿黑丝高跟| 少妇丰满av| 日韩欧美精品v在线| 成人永久免费在线观看视频| 国产激情欧美一区二区| 很黄的视频免费| 日韩欧美精品免费久久 | 久久人妻av系列| 成年免费大片在线观看| 最近最新中文字幕大全免费视频| 色综合站精品国产| 久久久久久九九精品二区国产| 久久国产精品人妻蜜桃| 国产久久久一区二区三区| 亚洲第一欧美日韩一区二区三区| 国产成人aa在线观看| 欧美日韩乱码在线| 久久久久久大精品| 日韩欧美一区二区三区在线观看| 日韩欧美精品v在线| 久久精品人妻少妇| av在线蜜桃| 女同久久另类99精品国产91| 一个人看视频在线观看www免费 | 欧美国产日韩亚洲一区| 性欧美人与动物交配| 亚洲五月天丁香| 欧美性感艳星| 久久久久久久久久黄片| 婷婷精品国产亚洲av在线| 成人国产综合亚洲| 午夜免费男女啪啪视频观看 | 亚洲成人免费电影在线观看| 网址你懂的国产日韩在线| 国产精品亚洲一级av第二区| 欧美日韩黄片免| 亚洲精品亚洲一区二区| 日本与韩国留学比较| 亚洲自拍偷在线| 美女免费视频网站| 久久精品国产亚洲av香蕉五月| 亚洲国产欧洲综合997久久,| 国产精品日韩av在线免费观看| 国产精品精品国产色婷婷| 观看美女的网站| 欧美黑人巨大hd| 亚洲成av人片免费观看| 桃红色精品国产亚洲av| 久久久久九九精品影院| 在线观看午夜福利视频| 日本与韩国留学比较| 国产午夜福利久久久久久| 欧美精品啪啪一区二区三区| 在线国产一区二区在线| 窝窝影院91人妻| 狂野欧美激情性xxxx| 老司机午夜福利在线观看视频| 一区福利在线观看| 亚洲国产精品合色在线| 欧美色欧美亚洲另类二区| 禁无遮挡网站| 国产欧美日韩一区二区精品| 一级作爱视频免费观看| 久久午夜亚洲精品久久| 欧美乱妇无乱码| 精品一区二区三区视频在线 | 成人欧美大片| 精品一区二区三区av网在线观看| 一级毛片女人18水好多| 99精品在免费线老司机午夜| 怎么达到女性高潮| 尤物成人国产欧美一区二区三区| 精品99又大又爽又粗少妇毛片 | 免费在线观看成人毛片| 免费看十八禁软件| 国产亚洲精品久久久com| 黄片小视频在线播放| 宅男免费午夜| 高清日韩中文字幕在线| 国产精品久久久久久精品电影| 男女下面进入的视频免费午夜| 久久亚洲精品不卡| 在线观看一区二区三区| 国产一区二区在线观看日韩 | 99久久九九国产精品国产免费| 校园春色视频在线观看| 欧美一级毛片孕妇| 精品午夜福利视频在线观看一区| 欧美极品一区二区三区四区| av片东京热男人的天堂| 欧美3d第一页| 最新在线观看一区二区三区| 性色av乱码一区二区三区2| 少妇裸体淫交视频免费看高清| 日本免费a在线| 制服丝袜大香蕉在线| 国产黄色小视频在线观看| 我要搜黄色片| 噜噜噜噜噜久久久久久91| 国产主播在线观看一区二区| 男女下面进入的视频免费午夜| 99国产极品粉嫩在线观看| 亚洲美女黄片视频| 国产野战对白在线观看| 人人妻人人澡欧美一区二区| 亚洲精品日韩在线中文字幕| 亚洲av中文av极速乱| 国产永久视频网站| 麻豆久久精品国产亚洲av| 美女脱内裤让男人舔精品视频| 久久久久久久久久人人人人人人| av福利片在线观看| 蜜臀久久99精品久久宅男| 午夜福利在线在线| 成人毛片a级毛片在线播放| 国产精品久久久久久久电影| 日韩在线高清观看一区二区三区| 精品久久久久久久人妻蜜臀av| 大又大粗又爽又黄少妇毛片口| 亚洲天堂国产精品一区在线| 中文字幕制服av| 欧美成人精品欧美一级黄| 韩国高清视频一区二区三区| 97精品久久久久久久久久精品| 老司机影院成人| 日韩成人av中文字幕在线观看| 99九九线精品视频在线观看视频| 欧美bdsm另类| 久久国产乱子免费精品| 美女大奶头视频| 亚洲精品日韩av片在线观看| 亚洲av中文av极速乱| 蜜臀久久99精品久久宅男| 亚洲欧美精品专区久久| 少妇丰满av| 国产不卡一卡二| 搡女人真爽免费视频火全软件| 黄片wwwwww| 床上黄色一级片| 成人漫画全彩无遮挡| 日韩强制内射视频| 一级毛片久久久久久久久女| 亚洲精品久久午夜乱码| 欧美成人一区二区免费高清观看| 国内精品宾馆在线| 99热全是精品| 男人狂女人下面高潮的视频| 亚洲精品乱码久久久v下载方式| 国产精品麻豆人妻色哟哟久久 | 真实男女啪啪啪动态图| 青春草视频在线免费观看| 国产精品人妻久久久久久| 国产一区二区三区综合在线观看 | 97精品久久久久久久久久精品| 三级毛片av免费| 亚洲久久久久久中文字幕| 在线播放无遮挡| 天堂中文最新版在线下载 | 精品国内亚洲2022精品成人| h日本视频在线播放| 日韩欧美精品v在线| av在线天堂中文字幕| 久久久色成人| 十八禁国产超污无遮挡网站| 少妇熟女aⅴ在线视频| 亚洲精品亚洲一区二区| 国产黄a三级三级三级人| 国内精品宾馆在线| 国产一级毛片在线| a级一级毛片免费在线观看| 欧美日韩综合久久久久久| 成年女人看的毛片在线观看| 亚洲av二区三区四区| 免费高清在线观看视频在线观看| 三级国产精品欧美在线观看| 神马国产精品三级电影在线观看| 国产高潮美女av| 日韩欧美三级三区| 国产黄片视频在线免费观看| 国产片特级美女逼逼视频| 久久久久久久久久久丰满| 久久久欧美国产精品| 国产一级毛片七仙女欲春2| 日本午夜av视频| 精品一区在线观看国产| 2021少妇久久久久久久久久久| 极品教师在线视频| 日日摸夜夜添夜夜添av毛片| 日韩人妻高清精品专区| av免费在线看不卡| 少妇猛男粗大的猛烈进出视频 | 亚洲va在线va天堂va国产| 亚洲精品国产av蜜桃| 97超碰精品成人国产| 在线观看av片永久免费下载| 美女黄网站色视频| 美女内射精品一级片tv| 极品少妇高潮喷水抽搐| 亚洲av二区三区四区| 日韩精品有码人妻一区| 国产高清有码在线观看视频| 美女高潮的动态| 久久亚洲国产成人精品v| 久久久午夜欧美精品| 91久久精品国产一区二区三区| 国产亚洲精品久久久com| 九九爱精品视频在线观看| 黄色配什么色好看| 欧美bdsm另类| 亚洲国产精品成人综合色| 麻豆精品久久久久久蜜桃| 久久久久久久久中文| 国产黄色免费在线视频| 狂野欧美激情性xxxx在线观看| 成人av在线播放网站| 黄色欧美视频在线观看| 成人毛片60女人毛片免费| 亚洲18禁久久av| 国内精品宾馆在线| 国产日韩欧美在线精品| 99视频精品全部免费 在线| 美女国产视频在线观看| 久久韩国三级中文字幕| 别揉我奶头 嗯啊视频| 久久久久久久久久人人人人人人| 99久久精品热视频| 欧美日韩国产mv在线观看视频 | 人人妻人人澡欧美一区二区| 淫秽高清视频在线观看| 在线免费观看不下载黄p国产| 国产成人精品一,二区| 你懂的网址亚洲精品在线观看| 我的女老师完整版在线观看| 久久国内精品自在自线图片| 黄色欧美视频在线观看| 精品人妻偷拍中文字幕| 淫秽高清视频在线观看| 国产视频内射| 日本熟妇午夜| 亚洲怡红院男人天堂| 午夜免费激情av| 一级爰片在线观看| 在线观看av片永久免费下载| 精品一区在线观看国产| 日本黄色片子视频| 精品久久久久久久久久久久久| 欧美+日韩+精品| 3wmmmm亚洲av在线观看| 男女视频在线观看网站免费| 国产精品一二三区在线看| 直男gayav资源| 成年女人看的毛片在线观看| 99久久中文字幕三级久久日本| 国模一区二区三区四区视频| 国产亚洲av片在线观看秒播厂 | 看非洲黑人一级黄片| 天天躁日日操中文字幕| 老师上课跳d突然被开到最大视频| 免费无遮挡裸体视频| 日韩制服骚丝袜av| 亚洲欧美清纯卡通| 国产成人精品一,二区| 国产爱豆传媒在线观看| 精品一区在线观看国产| 亚洲精品第二区| 亚洲欧美日韩东京热| 国产成人91sexporn| 国产老妇伦熟女老妇高清| 亚洲精华国产精华液的使用体验| 国内少妇人妻偷人精品xxx网站| 成人特级av手机在线观看| 亚洲一区高清亚洲精品| 国产精品一区二区在线观看99 | 成人午夜高清在线视频| 精品久久久久久久久久久久久| 国产精品1区2区在线观看.| 国产精品一及| 国产片特级美女逼逼视频| 国产在线男女| 中文欧美无线码| 中国国产av一级| 免费看日本二区| 国产成人freesex在线| 久久这里只有精品中国| 午夜老司机福利剧场| 欧美一级a爱片免费观看看| 国产精品综合久久久久久久免费| a级毛片免费高清观看在线播放| 免费看av在线观看网站| 看免费成人av毛片| 久久久久久久久久黄片| 免费在线观看成人毛片| 九草在线视频观看| 日韩大片免费观看网站| 亚洲欧美一区二区三区国产| 尾随美女入室| 亚洲精品成人久久久久久| 久久久久九九精品影院| 国产免费又黄又爽又色| 搡女人真爽免费视频火全软件| 女人被狂操c到高潮| 日韩av在线免费看完整版不卡| 美女大奶头视频| 高清欧美精品videossex| 成人亚洲精品av一区二区| 寂寞人妻少妇视频99o| 亚洲精品国产成人久久av| 极品教师在线视频| 亚洲欧美精品自产自拍| 免费看美女性在线毛片视频| 精品亚洲乱码少妇综合久久| 亚洲欧美一区二区三区黑人 | 国产亚洲精品av在线| 亚洲美女视频黄频| 欧美xxxx性猛交bbbb| 免费看不卡的av| 中文字幕av成人在线电影| 日韩av免费高清视频| 插阴视频在线观看视频| 欧美高清性xxxxhd video| 国产精品99久久久久久久久| 国产av在哪里看| 一级毛片电影观看| 麻豆成人午夜福利视频| 国产 一区 欧美 日韩| 大香蕉久久网| 日韩伦理黄色片| 成人午夜高清在线视频| 欧美3d第一页| 午夜免费男女啪啪视频观看| 免费观看av网站的网址| 我的女老师完整版在线观看| 丰满少妇做爰视频| 尤物成人国产欧美一区二区三区| 三级经典国产精品| eeuss影院久久| 91在线精品国自产拍蜜月| 免费看日本二区| 亚洲色图av天堂| 国产真实伦视频高清在线观看| 一级毛片久久久久久久久女| 国产一区有黄有色的免费视频 | 国产亚洲最大av| 日日啪夜夜爽| 亚洲成人精品中文字幕电影| 国产精品嫩草影院av在线观看| 久久鲁丝午夜福利片| 亚洲国产欧美人成| 精品人妻一区二区三区麻豆| 亚洲成人精品中文字幕电影| 精品欧美国产一区二区三| 岛国毛片在线播放| 精品一区在线观看国产| 国产高清三级在线| 美女主播在线视频| 非洲黑人性xxxx精品又粗又长| 老司机影院毛片| 国产黄色小视频在线观看| 99久久精品一区二区三区| 国产成人免费观看mmmm| 日本黄色片子视频| 国产精品综合久久久久久久免费| 国产成人a∨麻豆精品| 国产伦理片在线播放av一区| 国产欧美另类精品又又久久亚洲欧美| 亚洲国产精品国产精品| 精华霜和精华液先用哪个| 乱系列少妇在线播放| 黄色日韩在线| 日本免费a在线| 久久久久久久久中文| 精品久久久久久久久亚洲| 97精品久久久久久久久久精品| 日本免费在线观看一区| 一区二区三区四区激情视频| 国产又色又爽无遮挡免| 又粗又硬又长又爽又黄的视频| 精品99又大又爽又粗少妇毛片| 国产极品天堂在线| 在现免费观看毛片| 看免费成人av毛片| 99九九线精品视频在线观看视频| 中文在线观看免费www的网站| 亚洲熟女精品中文字幕| 一级黄片播放器| 一区二区三区高清视频在线| 午夜福利视频1000在线观看| 三级男女做爰猛烈吃奶摸视频| 美女xxoo啪啪120秒动态图| 成人综合一区亚洲| 久久久久久伊人网av| 内地一区二区视频在线| 亚洲精品aⅴ在线观看| 一区二区三区乱码不卡18| 亚洲最大成人中文| 综合色丁香网| 日韩成人伦理影院| 嫩草影院精品99| a级一级毛片免费在线观看| 777米奇影视久久| 国产亚洲av片在线观看秒播厂 | 午夜亚洲福利在线播放| 亚洲人成网站在线观看播放| 国产欧美另类精品又又久久亚洲欧美| 亚洲av在线观看美女高潮| 亚洲欧美成人综合另类久久久| 亚洲一区高清亚洲精品| 国产av在哪里看| 一级黄片播放器| ponron亚洲| 成人av在线播放网站| 身体一侧抽搐| 日本欧美国产在线视频| 大陆偷拍与自拍| av卡一久久| 黄色日韩在线| 亚洲精品影视一区二区三区av| 亚洲性久久影院| 我要看日韩黄色一级片| 天堂av国产一区二区熟女人妻| 久久久国产一区二区| 亚洲三级黄色毛片| 亚洲av成人av| 亚洲精品一区蜜桃| 精品久久久久久电影网| 国产乱人偷精品视频| 国产成人91sexporn| 亚洲国产日韩欧美精品在线观看| 国产精品一及| 久久久a久久爽久久v久久| 色吧在线观看| 国产 一区 欧美 日韩| 亚洲国产av新网站| 亚洲欧美一区二区三区国产| 男的添女的下面高潮视频| 国产精品嫩草影院av在线观看| 高清午夜精品一区二区三区| 亚洲va在线va天堂va国产| 国产白丝娇喘喷水9色精品| 我要看日韩黄色一级片| 亚洲无线观看免费| 成人漫画全彩无遮挡| 日韩在线高清观看一区二区三区| 淫秽高清视频在线观看| 波多野结衣巨乳人妻| 91久久精品国产一区二区三区| 看黄色毛片网站| 国产高清国产精品国产三级 | 99久久中文字幕三级久久日本| 亚洲精品乱码久久久v下载方式| 哪个播放器可以免费观看大片| 超碰97精品在线观看| 日本与韩国留学比较| 国产精品国产三级国产专区5o| av在线观看视频网站免费| 又爽又黄无遮挡网站| 亚洲欧美日韩无卡精品| 晚上一个人看的免费电影| 亚洲av成人精品一二三区| 亚洲av在线观看美女高潮| 久久99热这里只有精品18| 在线观看人妻少妇| 亚洲自偷自拍三级| 精品国内亚洲2022精品成人| 夫妻午夜视频| 亚洲精华国产精华液的使用体验| av在线天堂中文字幕| 伊人久久精品亚洲午夜| 在线观看免费高清a一片| 亚洲av二区三区四区| 最后的刺客免费高清国语| av.在线天堂| 麻豆成人午夜福利视频| 日韩av在线免费看完整版不卡|