• <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 ?

    Highly selective oxidation of amines to imines by Mn2O3 catalyst under eco-friendly conditions

    2020-01-14 07:55:26FushnChenToYngSonglinZhoTotoJingLuYuHoufengXiongChunkunGuoYufngRoYnLiuLiuLiuJinZhouPengxingTuJunNiQunfengZhngXioninLi
    Chinese Chemical Letters 2019年12期

    Fushn Chen,To Yng,Songlin Zho,Toto Jing,Lu Yu,Houfeng Xiong,Chunkun Guo,Yufng Ro,Yn Liu,Liu Liu,Jin Zhou,Pengxing Tu,Jun Ni,Qunfeng Zhng,*,Xionin Li

    a Industrial Catalysis Institute of Zhejiang University of Technology, Hangzhou 310014, China

    b Jiangxi Province Engineering Research Center of Ecological Chemical Industry, Jiujiang University, Jiujiang 332005, China

    c School of Pharmaceutical and Chemical Engineering, Taizhou University, Taizhou 318000, China

    Keywords:

    Oxalate route

    Mn2O3

    Self-coupling of amines

    Heterogeneous catalysis

    Aerobic oxidation

    ABSTRACT

    Enhancing the selectivity of imines for the oxidative self-coupling of primary amines was found to be challenging in the heterogeneous catalysis.Three different manganese oxides(M-3,M-4,M-5)were synthesized by controlling the calcination temperature using a simple template-free oxalate route.The prepared manganese oxides were systematically characterized using XRD, N2 sorption, SEM, TEM,XPS,H2-TPR techniques.M-4 gave 96.2%selectivity of imine at 100%conversion of benzylamine,which was far more superior than other existing protocols.Mn3+/Mn4+ ratio was found to affect the selectivity of the imines.The probable reaction pathway for amines oxidation catalyzed by manganese oxides was proposed for the first time.

    Imines, as Schiff bases, are well known as a very versatile intermediate that are widely applied in the production of pesticides, medicine, and so on [1,2].Conventional synthetic method of imines usually involves condensation reaction between amines and carbonyl compounds,and requires unstable aldehydes,Lewis acid catalysts,and dehydrating agents[1,3],which restricted the practical use of this method [4].

    The oxidative self-coupling of amines to imines was one of the most efficient methodologies [1].However, most of the reported protocols required hazardous stoichiometric oxidants such as permanganate, chromate, and 2-iodoxybenzoic acid, which was undesirable from the perspective of green chemistry [3,5].Replacement of these undesired oxidants with green oxidants like air or O2is an attractive and active research area.In the past decade, various heterogeneous catalysts have been applied to the self-coupling of primary amines, including catalysts based on Pt[6],Pd[7],Ru[8],Au[9],V[10],Cu[11],as well as other catalytic systems employing MOF[12],GO[13],and photocatalysts[14,15],etc.However, despite the satisfying conversions obtained using some of the systems, most of them either required complicated synthetic procedure of catalysts, precious metal, toxic catalysts,harsh reaction conditions, light irradiation, prolonged reaction time, alkali addition, or suffered from poor reusability of the catalysts,and poor selectivity due to the formation of by-products.Therefore, effective heterogeneous catalytic system for the oxidative self-coupling of amines has long been required to overcome the problems mentioned above.

    Among the available metal oxides,manganese oxides are cheap,non-toxic, and are effective for many catalytic processes, such as selective oxidation of various organic compounds [2,16-22], CO oxidation[23],and water-splitting reaction[24].Manganese oxide had superior catalytic activity due to the abundant active sites(Mn3+)it possesses, as well as excellent redox properties resulted from its multi-valency,weaker metal-oxygen bond it forms,and its rich lattice oxygen content with higher mobility [2,17,25].

    Enhancing the selectivity of imines for the oxidative self-coupling of amines was found challenging[19,26,27].High amine conversion was normally accompanied with the formation of by-products including nitrile, aldehyde, amide in the formation of imine [19].Precipitation was one of the most favorite methods for catalyst preparation in large scale.Recently,Our latest research showed that Mn4+in manganese oxides through simple oxalate route was responsible for the excessive oxidation of quinoline,while Mn3+in manganese oxides displayed remarkable catalytic activity towards oxidative dehydrogenation of 1,2,3,4-tetrahydroquinoline[28].The valence distribution of manganese was a key factor to the high selectivity of quinoline.In this work, we prepared different manganese oxides bya simple oxalate route.The manganese oxalate calcined at a certain temperature (350°C, 450°C, 550°C) were denoted M-3,M-4,M-5.Detailed methods for catalyst preparation,characterization and evaluation were summarized in Supporting information.The structure and morphology of the catalyst were characterizedby XRD,N2sorption,SEM,TEM,and the results showed that M-3 was mesoporous Mn2O3microrod with moderate surface area(Fig.1,Table S1 and Figs.S1-S3 in Supporting information).As a novel attemptation for oxidation of benzylamine to imine, 100%conversion of benzylamine and 96.2% selectivity of imine were successfully achieved with M-3 catalyst in 2 h,which was far more superior than other existing protocols.Furthermore, this catalytic process was carried out under milder conditions,no base additives,and air as the only oxidant.

    The X-ray diffraction patterns of the samples were showed in Fig.1.M-3 exhibited no distinct diffraction peak in Fig.1, which suggested the amorphous nature of the material.Sample M-4 showed clearly appeared diffraction peaks,which were consistent with the main cubic crystal Mn2O3((JCPDS Card No.041-1442)and a small part of metastable Mn5O8(JCPDS Card No.039-1218).Sample M-5 only showed enhanced diffraction peaks of Mn2O3.The results implied that the crystal particle size of manganese oxides increased with calcination temperature elevated(Table S1).

    The surface elemental compositions were analyzed by using XPS.Fig.2 displayed the Mn2p and O 1sXPS spectra of various catalysts.It was well known that the deconvolution of Mn2p3/2andMn2p1/2XPS spectra was useful to distinguish the oxidation states of Mnn+.As shown in Fig.2a,the Mn 2p2/3XPS spectra on the surface of catalysts showed a broad shoulder peak, which implied the coexistence of Mn2+, Mn3+and Mn4+species.The fitted Mn 2p3/2peaks at the binding energy (BE) of 643.0 eV, 641.7 eV, and 640.6 eV could be assigned to Mn4+,Mn3+,and Mn2+,respectively(Fig.2a)[29,30].A spin-orbit energy separation(11.7±0.2 eV)was displayed between Mn 2p1/2and Mn 2p3/2states (Fig.2a).Fig.2b showed the asymmetrical peak, which could be seen as the superposition of three peaks of O 1s at 533.0 eV,531.3 eV,529.8 eV.The small peak at BE of 533.0 eV was the characteristic of the molecular water(named as Osuf),the peak at BE of 531.3 eV corresponded to adsorbed oxygen species(O2-,O22-,O-,named as Oads),and the peak at BEof 529.8 eV was indexed to lattice oxygen atoms in Mn-O-Mn (O2-, named as Olatt) [29-31].Table 1 showed surface Mnn+and different surface oxygen species molar fraction from Mn 2p and O 1s XPS spectra.Surface-active Mn3+species had an important influence on the catalytic activity of the oxidative self-coupling of amines to imines[19].In our latest research, we had found that Mn4+easily led to excessive oxidation of quinoline[28].As could be interestingly seen from Table 1, M-4 possessed highest content of Mn3+(0.486) and highest Mn3+/Mn4+ratio,implying that M-4 possessed the moderate catalytic activity and higher selectivity of imines.Table1 showed that M-4 owned highest content of water in surface oxygen compared with the other samples.The role of water on manganese oxide surface was also believed to be significant for amine oxidation to imine[19].

    Fig.1.XRD patterns of wide angle (10°-80°) of the samples.

    Fig.2.Mn 2p and O 1s XPS spectra of various catalysts.

    Table 1 Parameters of the fitted components on surface from Mn 2p and O 1s XPS spectra.

    The catalytic activities of different manganese oxides were evaluated using the oxidative self-coupling of benzylamine as a model reaction.The evaluating results were shown in Table 2.The reaction hardly happened in the absence of catalyst(Table 2,entry 1).No products were detected using Mn(NO3)2,Mn(C2O4)·3H2O as the catalysts(Table 2, entries 2 and 3).Surprisingly,not only M-4 catalyst achieved 100% conversion of benzylamine, but also the selectivity of imine was as high as 96.2% (Table 2, entry 5).Concerning the solvent (Table S2 in Supporting information,entries 1-5),toluene solvent could provide higher conversion and selectivity.The by-product was mainly benzonitrile in toluene as the solvent, in addition to a small amount of benzaldehyde and benzamide.At 100% conversion of benzylamine, the selectivity to imine was only 77.2%by M-3 catalyst(Table 2,entry 4).When the conversion of benzylamine was 80.3%, the highest selectivity(98.3%)of imine was achieved using M-5 catalyst(Table 2,entry 6),implying that the imine showed higher selectivity at low conversion of benzylamine after 2 h of the reaction.These results suggested manganese oxide calcined at low temperature showed high catalytic activity for oxidation of amine,and manganese oxide calcined at high temperature showed high selectivity to imine.Although this reaction process produced water, the addition of trace water increased the selectivity of the imine(Table 2,entry 7,Fig.3b).This suggested that trace water was beneficial to the formation of imines during the reaction,which was also consistent with the literature [19].Under O2atmosphere, M-4 achieved the enhanced conversion(98.8%)and the decreased selectivity(94.2%)after 1 h (Table 2, entry 8, Fig.3a).N2atmosphere only gave 6.3%conversion(Table 2,entry 9),which ascribed the oxidation role of active oxygen species in the manganese oxide [32].

    The selectivity of imine was an important issue in the oxidation of benzylamine[19].Figs.3a-c showed catalytic activity of M-4,M-3,and M-5 dependent on the reaction time.M-4 gave 100%conversion of benzylamine and 96.2% selectivity of imine in 2 h, and the selectivity of imine slightly decreased when the reaction time was further prolonged (Fig.3a).M-3 gave 99.5% conversion of benzylamine and90.1%selectivity of imine for 1 h(Fig.3b).Theselectivityof imine sharply decreased by M-3 with the reaction time being prolonged, and the selectivity of by-product benzonitrile rapidly increased.Compared with M-3 and M-4, benzylamine conversion with M-5 catalyst significantly decreased at the same reaction time(Fig.3c).M-5gaveonly80.3%conversionand98.3%selectivityfor2 h,and the selectivity of imine also slightly decreased extending the reaction time to 4 h.These results further confirmed that M-4 was the best catalyst for the oxidation of benzylamine to imine.Testing of the different amount of catalyst(Table S3 in Supporting information),and different reaction temperatures (Table S4 in Supporting information) also confirmed that M-4 was the most effective catalyst.Compared with various manganese-based catalysts from the reported literature (Table S5 in Supporting information),undoped M-4 in our work not only achieved the higher conversion,but also gave the higher selectivity.

    Table 2 Imine synthesis from benzylamine over the as prepared catalysts.a

    Fig.3.Catalytic activity of catalysts(a)M-4,(b)M-3,(c)M-5 dependent on the reaction time.Reaction conditions:benzylamine(1.0 mmol),catalyst(25 mg),toluene(5.0 mL),110°C, air balloon.

    The recyclability and heterogeneity of M-4 had been investigated by using benzylamine as the test substrate (Figs.S5-S8 in Supporting information).Each cycle gave good conversion and hardly significantly reduced selectivity (Fig.S5).Figs.S7 and S8 showed that the XRD pattern, Mn 2p XPS spectra of third reused M-4 displayed no significant change compared with that of the fresh catalyst.In addition, Mn3+/Mn4+ratio did not significantly change in M-4(Table 1,entries 2 and 4).To explore the leaching of active species,the hot filtration survey was also carried out.After the catalyst was removed at 76.0% conversion, the conversion of benzylamine had not been further improved (Fig.S6).It could be inferred from these results that M-4 was reusability, and authentically heterogeneous nature.

    With the establishment of optimized conditions,the substrate scope and limitations were investigated using M-4 catalyst.The evaluation data of the oxidative self-coupling of a variety of amines, including aromatic, aliphatic amines, was showed in Table 3.M-4 was able to catalyze aromatic(Table 3,entries 1-5),aliphatic (Table 3, entries 6 and 7) amines to the corresponding imines.However, much longer reaction time was required for achieving good yields in the oxidation of substituted benzylamines (Table 3, entries 2-4).Surprisingly, 2-thiophenemethylamine gave 99.3%conversion and 97.0%selectivity in 3 h(Table 3,entry 5).Aliphatic amines showed very low conversion (Table 3,entries 6-7), as was due to the lack of active groups attached to NH2of the aliphatic amines [27].

    Table 3 The synthesis of imines from various amines by the M-4 catalyst.a

    According to the evaluation results of the catalysts, benzylamine could produce product imine, as well as by-product benzaldehyde,benzonitrile,benzamide during the reaction.When benzylamine was highly or completely converted, the amount of benzonitrile would quickly increase.According to the literature[27], benzylamine would form the imine intermediate during the oxidation process,but it was not detected in the reaction.It might be because the imine intermediate from the oxidation of benzylamine was very unstable, and it was hydrolyzed to form benzaldehyde by the water formed in situ.According to literature[27]and experiments,we first proposed the more possible reaction pathway followed the oxidation of amines as shown in Scheme 1.In general,the oxidative dehydrogenation pathway was suggested for the oxidation of amines.An imine intermediate was formed from initial amine(step I),and then hydrolyzed by water generated in situ to give an aldehyde(step II).The formed aldehyde instantly reacted with available amine to yield the final imine (step III).Simultaneously, the by-product benzonitrile was formed by further oxidation of a very small amount of imine intermediate(step VI).The trace benzonitrile could be hydrolyzed to give the amide (step VII).When the initial amine molecules were almost converted,the aldehyde formed from the reverse reaction of imine could not be effectively condensed with the trace amine,but could be condensed with ammonia molecules generated in situ to form imine intermediates(step V).Reversible amines were also oxidized to imine intermediates (step I).The small part of imine intermediates were hydrolyzed to form aldehydes (step II), and the other part were further oxidized to form nitriles(step VI),and a small amount of nitriles were hydrolyzed to form amides(step VII).As the process was continuously circulated,the selectivity of imine continued to decrease, and the selectivity of benzonitrile and benzamide continues to increase.The speculation was well confirmed by the experimental results.

    Scheme 1.Possible reaction pathway for the oxidation of amines.

    It was well known that the catalytic activity of manganese oxide was determined by several factors such as lattice oxygen,adsorbed oxygen, oxygen vacancy, surface oxidation state of manganese,mobility of lattice oxygen,texture properties,and so on [1,19,27-29,32,33].By comparing the structure-activity relationship, we found that Mn4+in manganese oxide might be strongest active sites, but easily led to excessive oxidation of benzylamine to benzonitrile.Mn3+might be the main active sites of benzylamine oxidation to imine,which was also confirmed by the literature[19].It was surprisingly found that the selectivity of imine was better when the Mn3+/Mn4+ratio was higher(Tables 1 and 2, Fig.S9 in Supporting information).Mn2+in manganese oxalate almost showed no catalytic activity (Table 2, entry 3).However, higher content of Mn2+in manganese oxide could generate more oxygen vacancies,and promoted aerobic oxidation[27].M-3 with highest specific surface area(304.7 m2/g)showed highest Mn4+content (0.386) compared with M-4 (0.254) and M-5 (0.273) (Table S1 and Table 1), resulting in highest catalytic activity and easy oxidizing imine intermediates to nitrile(Table 2,Fig.3).Although it gave lower Mn4+content (0.254), M-4 with sharply reduced surface area(28.4 m2/g)showed slight reduction in catalytic activity.This was because Mn2+content (0.260)significantly increased to generate more oxygen vacancies,which promoted aerobic oxidation.Higher water molecules (0.143)among surface oxygen species on the M-4 surface promoted hydrolysis of the imine intermediate to aldehyde (Scheme 1,step II), which further reacted with another amine to form the product imine(Scheme 1)[19].This might be another important reason for higher activity and selectivity of M-4.The addition of trace water increased the selectivity of the imine in the process of using M-3 as the catalyst(Table 2,entries 4 and 7),which further confirmed that water played a positive role in the reaction process.Trace water weakened further oxidation of the imine intermediate to form a nitrile (Scheme 1, step VI).M-5 gave the lowest catalytic activity, which might be related to lower Mn4+content(0.273),lowest surface area(19.4 m2/g),lowest content of water molecules (0.045) among surface oxygen species.Manganese oxides displayed a two-step reduction (Mn2O3(MnO2) →Mn3O4→MnO) (Fig.S4 from H2-TPR in Supporting information) [34].The lattice oxygen mobility of the catalysts could be associated with the ease of the manganese oxides reducibility, which played an important role on the catalytic oxidation reactions[16,29,34].Fig.S4 implied that M-5 possessed lowest lattice oxygen mobility, which might also be the important reasons for lowest activity of M-5.In addition, the selectivity of imines might be related to pore diameter(Table S1,Fig.S1, Table 2), and larger pore size facilitated the diffusion of larger imine molecules.

    According to experimental results and the literature [19], We suggested a mechanism for the oxidative self-coupling of amines catalyzed by M-4 (Scheme S1 in Supporting information).An electron of adsorbed amine molecules was transferred to Mn4+/Mn3+(Mn4+/Mn3+→Mn3+/Mn2+), and an α-C-H proton and N--H proton were eliminated to generate the RCH=NH intermediate (Scheme S2 in Supporting information).In this process, the rate-determining step was the abstraction of α-C-H proton (Scheme S2).One-electron reduction of Mn4+/Mn3+could facilitate release of lattice oxygen.The reduced Mn species could be re-oxidized to Mn4+/Mn3+by O2decomposed from H2O2in the aid of manganese oxide [35].The aerobic atmosphere was crucial for the catalytic activity because replenishment of the consumed lattice oxygen required aerial oxygen.This was consistent with the observation of lower catalytic efficiency under nitrogen atmosphere (Table 2, entry 9).

    In summary, we had successfully developed the manganese oxide catalyst showing higher selectivity of amines to imines by simple oxalate route.Characterization of M-4 showed that it had micro-rod morphology, large average pore diameter, moderate lattice oxygen mobility, highest content of water in surface oxygen species,high Mn3+/Mn4+ratio,and was mainly composed of cubic crystal Mn2O3.The enhanced selectivity of M-4 catalyst was attributed to the high Mn3+/Mn4+ratio and content of water among surface oxygen species.Besides, various substituted imines could also be synthesized with improved selectivity using the synthetic method introduced herein.Further investigations were underway.

    Acknowledgments

    Financial support from the National Natural Science Foundation of China (NSFC, Nos.21776258, 21476207, 91534113, 21406199,21566013, 21875220), Program from Science and Technology Department of Zhejiang Province (Nos.2015C31042,LY17B060006), Education Science Planning Project of Jiangxi Province(No.18YB243),and Natural Science Foundation of Jiangxi Province (No.20181BAB216032) are gratefully acknowledged.

    Appendix A.Supplementary data

    Supplementary material related to this article can be found,in the online version,at doi:https://doi.org/10.1016/j.cclet.2019.09.007.

    一个人观看的视频www高清免费观看| 91狼人影院| 欧美日韩综合久久久久久| 日产精品乱码卡一卡2卡三| 亚洲熟妇中文字幕五十中出| 性色avwww在线观看| 97超级碰碰碰精品色视频在线观看| av在线老鸭窝| 我的老师免费观看完整版| 少妇丰满av| 一个人免费在线观看电影| 亚洲国产色片| 亚洲人成网站在线观看播放| 国产精品一区二区性色av| 91麻豆精品激情在线观看国产| 免费观看人在逋| 狂野欧美白嫩少妇大欣赏| 亚洲欧美日韩高清在线视频| 欧美三级亚洲精品| 国产精品一区二区三区四区久久| 午夜精品在线福利| 99久久精品一区二区三区| 不卡一级毛片| 男女边吃奶边做爰视频| 精品无人区乱码1区二区| 国产精品电影一区二区三区| 12—13女人毛片做爰片一| 亚洲18禁久久av| 男人的好看免费观看在线视频| 亚洲人成网站在线播| 国产免费男女视频| 黄片wwwwww| 丰满乱子伦码专区| 99热精品在线国产| 三级国产精品欧美在线观看| 国产精品三级大全| 成人av在线播放网站| 晚上一个人看的免费电影| 日日撸夜夜添| 波野结衣二区三区在线| 黄色一级大片看看| 久久精品国产亚洲av涩爱 | 亚洲精品色激情综合| 一夜夜www| av在线播放精品| 18禁在线无遮挡免费观看视频 | 久久久久国产网址| 国产精品久久久久久久电影| 99久久久亚洲精品蜜臀av| 色哟哟哟哟哟哟| 在线观看一区二区三区| 亚洲精品色激情综合| 激情 狠狠 欧美| 免费大片18禁| 久久精品影院6| 精品免费久久久久久久清纯| 久久久久国内视频| 男人和女人高潮做爰伦理| 国产成人影院久久av| 一级黄片播放器| 亚洲人成网站在线播| 久久久久久久久久久丰满| 欧美绝顶高潮抽搐喷水| 久久久久国产网址| 22中文网久久字幕| 91av网一区二区| 最新中文字幕久久久久| 乱人视频在线观看| 一区二区三区四区激情视频 | 亚洲va在线va天堂va国产| 晚上一个人看的免费电影| 亚洲人成网站高清观看| 国产精品99久久久久久久久| 日韩国内少妇激情av| .国产精品久久| 色哟哟哟哟哟哟| 91午夜精品亚洲一区二区三区| 一级a爱片免费观看的视频| 久久精品久久久久久噜噜老黄 | 亚洲成av人片在线播放无| 伦理电影大哥的女人| 三级国产精品欧美在线观看| 国产精品无大码| 精品一区二区免费观看| 亚洲性夜色夜夜综合| 免费观看人在逋| 午夜爱爱视频在线播放| 伦精品一区二区三区| 成人三级黄色视频| 俺也久久电影网| 国内精品久久久久精免费| 我的老师免费观看完整版| 男女边吃奶边做爰视频| 成年免费大片在线观看| 亚洲经典国产精华液单| 亚洲精品粉嫩美女一区| 干丝袜人妻中文字幕| 一个人看视频在线观看www免费| 精品人妻视频免费看| 搡老妇女老女人老熟妇| 免费黄网站久久成人精品| 男人舔奶头视频| 免费av观看视频| 日韩在线高清观看一区二区三区| 午夜视频国产福利| 免费一级毛片在线播放高清视频| 亚洲国产精品成人综合色| 成人午夜高清在线视频| 性色avwww在线观看| 在线看三级毛片| 色尼玛亚洲综合影院| 国产精品人妻久久久久久| av天堂中文字幕网| 久久欧美精品欧美久久欧美| 亚洲欧美成人综合另类久久久 | 国内精品久久久久精免费| 日韩国内少妇激情av| 日本免费一区二区三区高清不卡| 亚洲性夜色夜夜综合| 亚洲欧美精品综合久久99| 国语自产精品视频在线第100页| www.色视频.com| 禁无遮挡网站| 亚洲性久久影院| 国内揄拍国产精品人妻在线| av女优亚洲男人天堂| 欧美高清成人免费视频www| 亚洲精品日韩av片在线观看| 春色校园在线视频观看| 国产成人一区二区在线| 久久久久久伊人网av| 久久国内精品自在自线图片| 午夜日韩欧美国产| 国产一区二区在线观看日韩| 97热精品久久久久久| 亚洲欧美日韩高清在线视频| 91av网一区二区| videossex国产| 午夜精品一区二区三区免费看| 亚洲av中文av极速乱| 校园人妻丝袜中文字幕| 成人美女网站在线观看视频| 亚洲成人精品中文字幕电影| 天天躁日日操中文字幕| 国产激情偷乱视频一区二区| 色噜噜av男人的天堂激情| 最后的刺客免费高清国语| 免费观看精品视频网站| eeuss影院久久| 日韩高清综合在线| av在线亚洲专区| 日韩精品有码人妻一区| 乱系列少妇在线播放| 久久久久久久久久成人| 精品午夜福利在线看| 一级黄片播放器| 日韩精品中文字幕看吧| 有码 亚洲区| 干丝袜人妻中文字幕| 婷婷精品国产亚洲av| 深夜精品福利| 女的被弄到高潮叫床怎么办| 国产高潮美女av| 一个人免费在线观看电影| 天堂影院成人在线观看| 亚洲av中文av极速乱| 欧美在线一区亚洲| 中文字幕av在线有码专区| 搡老岳熟女国产| 亚洲精品国产av成人精品 | 欧美日韩乱码在线| 精品一区二区三区av网在线观看| eeuss影院久久| 99久国产av精品国产电影| 日韩在线高清观看一区二区三区| 日韩欧美三级三区| 国产精品久久久久久久久免| 精品一区二区三区人妻视频| 欧美激情在线99| 亚洲在线观看片| 蜜臀久久99精品久久宅男| 天天躁日日操中文字幕| 搡老熟女国产l中国老女人| 久久这里只有精品中国| 国产中年淑女户外野战色| 久久久久国产精品人妻aⅴ院| 久久久久久久久久黄片| 国产v大片淫在线免费观看| 亚洲中文字幕日韩| 男女之事视频高清在线观看| 啦啦啦韩国在线观看视频| 国产午夜精品久久久久久一区二区三区 | 俺也久久电影网| 久久久久久久久中文| 少妇丰满av| 亚洲人成网站在线观看播放| 婷婷色综合大香蕉| 狂野欧美白嫩少妇大欣赏| 网址你懂的国产日韩在线| 床上黄色一级片| 免费看日本二区| 午夜福利在线观看免费完整高清在 | 午夜亚洲福利在线播放| 国产欧美日韩精品一区二区| av中文乱码字幕在线| 性插视频无遮挡在线免费观看| 啦啦啦观看免费观看视频高清| 成人三级黄色视频| 久久天躁狠狠躁夜夜2o2o| 国产精品久久电影中文字幕| 此物有八面人人有两片| 国产成人91sexporn| 哪里可以看免费的av片| 日韩欧美 国产精品| 最新中文字幕久久久久| 嫩草影院新地址| 欧美另类亚洲清纯唯美| 日本熟妇午夜| 欧美日本亚洲视频在线播放| 狂野欧美激情性xxxx在线观看| 俺也久久电影网| 啦啦啦韩国在线观看视频| 又粗又爽又猛毛片免费看| АⅤ资源中文在线天堂| 床上黄色一级片| 能在线免费观看的黄片| 国产精品一区二区免费欧美| 熟妇人妻久久中文字幕3abv| 欧美一区二区精品小视频在线| avwww免费| 日本a在线网址| 成熟少妇高潮喷水视频| 欧美高清成人免费视频www| 亚洲中文字幕日韩| 久久亚洲精品不卡| 亚洲欧美清纯卡通| 午夜精品一区二区三区免费看| 淫妇啪啪啪对白视频| 美女高潮的动态| 国产激情偷乱视频一区二区| 成人av一区二区三区在线看| 变态另类丝袜制服| 午夜福利在线观看吧| 人妻久久中文字幕网| 99久久九九国产精品国产免费| 少妇丰满av| 午夜福利在线观看吧| 精品一区二区三区av网在线观看| 永久网站在线| 亚洲熟妇熟女久久| 成人性生交大片免费视频hd| a级一级毛片免费在线观看| ponron亚洲| 男女边吃奶边做爰视频| 在线看三级毛片| 伦理电影大哥的女人| 91久久精品国产一区二区三区| 亚洲国产精品国产精品| 3wmmmm亚洲av在线观看| 干丝袜人妻中文字幕| 日韩欧美 国产精品| 精品久久久久久久末码| 99久久九九国产精品国产免费| 国产一区二区在线av高清观看| 久久人人爽人人片av| 又黄又爽又刺激的免费视频.| 夜夜夜夜夜久久久久| 亚洲精品一卡2卡三卡4卡5卡| 亚洲精品日韩av片在线观看| 精品乱码久久久久久99久播| 国产日本99.免费观看| 大香蕉久久网| 搡老岳熟女国产| 黄色视频,在线免费观看| 午夜激情欧美在线| 可以在线观看毛片的网站| 日韩欧美精品v在线| 99国产精品一区二区蜜桃av| 久久久a久久爽久久v久久| 国产亚洲精品久久久久久毛片| 日本精品一区二区三区蜜桃| 亚洲精品久久国产高清桃花| 国产 一区 欧美 日韩| 日韩欧美 国产精品| 嫩草影院精品99| 亚洲精品乱码久久久v下载方式| 亚洲第一区二区三区不卡| 国产国拍精品亚洲av在线观看| 99热6这里只有精品| 在现免费观看毛片| 级片在线观看| 国产 一区精品| 偷拍熟女少妇极品色| 老师上课跳d突然被开到最大视频| 日日啪夜夜撸| 成人无遮挡网站| 国产亚洲精品av在线| 久久这里只有精品中国| 午夜激情欧美在线| 黄色日韩在线| 深夜精品福利| 欧美成人免费av一区二区三区| 国产午夜福利久久久久久| 国产一区二区三区在线臀色熟女| 久久精品国产99精品国产亚洲性色| 伊人久久精品亚洲午夜| 婷婷色综合大香蕉| 美女cb高潮喷水在线观看| 国产探花极品一区二区| or卡值多少钱| 欧美高清成人免费视频www| 十八禁网站免费在线| 亚洲天堂国产精品一区在线| 一进一出好大好爽视频| 日本在线视频免费播放| 菩萨蛮人人尽说江南好唐韦庄 | 日日撸夜夜添| 中文字幕人妻熟人妻熟丝袜美| 久久精品久久久久久噜噜老黄 | 51国产日韩欧美| 人妻夜夜爽99麻豆av| 国产成人影院久久av| 国产黄片美女视频| 少妇裸体淫交视频免费看高清| 午夜免费男女啪啪视频观看 | 国产成人freesex在线 | 欧美三级亚洲精品| 美女cb高潮喷水在线观看| 亚洲成人av在线免费| 男女视频在线观看网站免费| 伦理电影大哥的女人| 亚洲七黄色美女视频| 色5月婷婷丁香| 综合色av麻豆| 中文资源天堂在线| 免费大片18禁| 波多野结衣巨乳人妻| 99在线人妻在线中文字幕| 久久人妻av系列| 色综合亚洲欧美另类图片| 亚洲美女搞黄在线观看 | 国内精品久久久久精免费| 在线免费观看的www视频| 精品99又大又爽又粗少妇毛片| 亚洲成人精品中文字幕电影| 老司机午夜福利在线观看视频| 国产午夜精品久久久久久一区二区三区 | 国产精品一区二区免费欧美| 国产精品一区二区三区四区久久| 大又大粗又爽又黄少妇毛片口| 亚洲av美国av| 国产成人a区在线观看| 一进一出好大好爽视频| 国产色爽女视频免费观看| 久久中文看片网| 乱码一卡2卡4卡精品| av国产免费在线观看| 国产亚洲欧美98| av天堂在线播放| 亚洲人与动物交配视频| av中文乱码字幕在线| 国产日本99.免费观看| 日韩人妻高清精品专区| 亚洲av熟女| 欧美高清成人免费视频www| 亚洲精品亚洲一区二区| 日韩国内少妇激情av| 国产黄a三级三级三级人| av黄色大香蕉| 午夜福利在线在线| 99国产精品一区二区蜜桃av| 联通29元200g的流量卡| 菩萨蛮人人尽说江南好唐韦庄 | 国产午夜精品论理片| 国产精品久久久久久精品电影| 精品人妻熟女av久视频| 三级经典国产精品| 色哟哟·www| 成年av动漫网址| 国内少妇人妻偷人精品xxx网站| 亚洲aⅴ乱码一区二区在线播放| 麻豆一二三区av精品| 久久99热这里只有精品18| 国产日本99.免费观看| 免费观看在线日韩| 日本爱情动作片www.在线观看 | 久久精品综合一区二区三区| 精品久久久久久久久久久久久| 自拍偷自拍亚洲精品老妇| 亚洲欧美日韩高清专用| 成年版毛片免费区| 国产精品精品国产色婷婷| 午夜精品一区二区三区免费看| 在线观看一区二区三区| 免费观看的影片在线观看| 真人做人爱边吃奶动态| 久久亚洲精品不卡| 亚洲成人久久爱视频| 国产毛片a区久久久久| 亚洲最大成人av| 国产 一区 欧美 日韩| 91av网一区二区| 熟女人妻精品中文字幕| 亚洲成人av在线免费| 日本免费a在线| 国产精品野战在线观看| 精品一区二区免费观看| 少妇熟女欧美另类| 久久精品91蜜桃| 国产高清有码在线观看视频| 国产伦精品一区二区三区四那| 我的女老师完整版在线观看| 亚洲av电影不卡..在线观看| 日本与韩国留学比较| 99在线视频只有这里精品首页| 成人特级黄色片久久久久久久| 老司机影院成人| 在线观看av片永久免费下载| 干丝袜人妻中文字幕| 3wmmmm亚洲av在线观看| 午夜久久久久精精品| 亚洲精品色激情综合| 99热精品在线国产| 深爱激情五月婷婷| 大香蕉久久网| 禁无遮挡网站| 男人舔奶头视频| 久久久国产成人精品二区| 日产精品乱码卡一卡2卡三| 免费看日本二区| 看非洲黑人一级黄片| 别揉我奶头 嗯啊视频| 日韩欧美一区二区三区在线观看| 国内精品久久久久精免费| 丰满乱子伦码专区| 一个人看视频在线观看www免费| 免费搜索国产男女视频| 免费观看在线日韩| 国产中年淑女户外野战色| 国产精品福利在线免费观看| 亚洲美女搞黄在线观看 | 成人精品一区二区免费| 嫩草影院新地址| 免费av不卡在线播放| 给我免费播放毛片高清在线观看| 亚洲精品日韩在线中文字幕 | 熟妇人妻久久中文字幕3abv| 嫩草影院入口| 国产女主播在线喷水免费视频网站 | 欧美激情久久久久久爽电影| 国模一区二区三区四区视频| 一区二区三区高清视频在线| 啦啦啦啦在线视频资源| 日韩欧美一区二区三区在线观看| 欧美最黄视频在线播放免费| 欧美性猛交╳xxx乱大交人| 亚洲欧美成人精品一区二区| 狂野欧美激情性xxxx在线观看| 欧美人与善性xxx| av卡一久久| 日本黄大片高清| 非洲黑人性xxxx精品又粗又长| 欧美日本亚洲视频在线播放| 别揉我奶头 嗯啊视频| 日韩欧美三级三区| 日韩在线高清观看一区二区三区| 午夜亚洲福利在线播放| 国产黄片美女视频| 精品一区二区三区视频在线| 国产精品无大码| 亚洲人成网站在线播| 99久久中文字幕三级久久日本| 美女被艹到高潮喷水动态| 激情 狠狠 欧美| 欧美不卡视频在线免费观看| 亚洲av免费高清在线观看| 此物有八面人人有两片| 精品午夜福利视频在线观看一区| 午夜a级毛片| 国产色爽女视频免费观看| 麻豆国产97在线/欧美| 在线国产一区二区在线| 深爱激情五月婷婷| 国产伦一二天堂av在线观看| 一级毛片久久久久久久久女| 在现免费观看毛片| 亚洲欧美清纯卡通| 不卡一级毛片| 日韩 亚洲 欧美在线| 日韩精品青青久久久久久| 一进一出抽搐动态| 久久欧美精品欧美久久欧美| 久久精品国产亚洲网站| 日韩av不卡免费在线播放| 精品无人区乱码1区二区| 国产精品综合久久久久久久免费| 午夜免费激情av| 插逼视频在线观看| 18禁裸乳无遮挡免费网站照片| 国产伦在线观看视频一区| 狠狠狠狠99中文字幕| 伦理电影大哥的女人| 日韩欧美精品免费久久| 在线观看免费视频日本深夜| 久久久久国内视频| 麻豆久久精品国产亚洲av| 国产片特级美女逼逼视频| 亚洲婷婷狠狠爱综合网| 看片在线看免费视频| 精品久久久久久久久av| 99热精品在线国产| 亚洲无线在线观看| 搡老熟女国产l中国老女人| av视频在线观看入口| 亚洲色图av天堂| 日韩高清综合在线| 身体一侧抽搐| 亚洲人与动物交配视频| 久久久午夜欧美精品| 一进一出抽搐动态| 国产三级中文精品| 干丝袜人妻中文字幕| 色噜噜av男人的天堂激情| 欧美国产日韩亚洲一区| 久久精品国产清高在天天线| 淫妇啪啪啪对白视频| 国产黄a三级三级三级人| 精品久久久久久久久久免费视频| 亚洲av成人av| 看片在线看免费视频| 日韩强制内射视频| 亚洲人成网站在线观看播放| 激情 狠狠 欧美| 91狼人影院| 嫩草影院新地址| 欧美不卡视频在线免费观看| 免费人成视频x8x8入口观看| 久久久久免费精品人妻一区二区| 偷拍熟女少妇极品色| 免费av观看视频| 亚洲性夜色夜夜综合| 欧美+日韩+精品| 日日干狠狠操夜夜爽| 国产白丝娇喘喷水9色精品| 六月丁香七月| 在线观看免费视频日本深夜| 久久九九热精品免费| 国产高潮美女av| 一级黄片播放器| 日韩欧美精品v在线| 中出人妻视频一区二区| 国内揄拍国产精品人妻在线| 亚洲第一电影网av| 美女黄网站色视频| av黄色大香蕉| 国产精品一区二区三区四区久久| 国产欧美日韩精品一区二区| 久久久精品欧美日韩精品| 欧美绝顶高潮抽搐喷水| 夜夜爽天天搞| h日本视频在线播放| 久久久久国内视频| 亚洲第一区二区三区不卡| 国产精品美女特级片免费视频播放器| 人人妻,人人澡人人爽秒播| 日本黄色片子视频| 亚洲精品成人久久久久久| 亚洲内射少妇av| 国产在视频线在精品| 免费不卡的大黄色大毛片视频在线观看 | 超碰av人人做人人爽久久| 国产精品99久久久久久久久| 69av精品久久久久久| 亚洲人成网站在线播放欧美日韩| 99在线视频只有这里精品首页| 久久欧美精品欧美久久欧美| 欧美中文日本在线观看视频| 男人舔女人下体高潮全视频| 亚洲天堂国产精品一区在线| 国产av不卡久久| 亚洲中文日韩欧美视频| 国产黄色小视频在线观看| 人人妻人人澡人人爽人人夜夜 | 天美传媒精品一区二区| 99久久九九国产精品国产免费| 日韩欧美精品免费久久| 久久人人精品亚洲av| 亚洲av成人精品一区久久| 99国产精品一区二区蜜桃av| 欧美又色又爽又黄视频| 99久久成人亚洲精品观看| 免费观看人在逋| 成人毛片a级毛片在线播放| 欧美极品一区二区三区四区| a级毛片a级免费在线| 亚洲av二区三区四区| 日本黄色片子视频| 97超视频在线观看视频| 国产精品国产高清国产av| 一级黄片播放器| 我的女老师完整版在线观看| 国产精品亚洲美女久久久| 国产真实乱freesex| 一进一出好大好爽视频| 国产成人freesex在线 | 精品久久久久久久久亚洲| 亚洲人成网站在线观看播放| 18禁裸乳无遮挡免费网站照片| av国产免费在线观看| 午夜视频国产福利| 性色avwww在线观看| 黄片wwwwww| 18+在线观看网站| 日本一二三区视频观看| 久久精品夜夜夜夜夜久久蜜豆|