• <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 ?

    Comparative study of adsorptive role of carbonaceous materials in removal of UV-active impurities of paclitaxel extracts☆

    2015-12-21 00:50:09JaberNasiriElahehMotamediMohammadRezaNaghavi
    Journal of Pharmaceutical Analysis 2015年6期

    Jaber Nasiri,Elaheh Motamedi,Mohammad Reza Naghavi

    Department of Agronomy and Plant Breeding,Division of Molecular Plant Genetics,College of Agricultural&Natural Resources,University of Tehran,Karaj,Iran

    Short Communication

    Comparative study of adsorptive role of carbonaceous materials in removal of UV-active impurities of paclitaxel extracts☆

    Jaber Nasiri,Elaheh Motamedi*,Mohammad Reza Naghavi**

    Department of Agronomy and Plant Breeding,Division of Molecular Plant Genetics,College of Agricultural&Natural Resources,University of Tehran,Karaj,Iran

    A R T I c L E I N F o

    Article history:

    25 March 2015

    Accepted 15 April2015

    Available online 24 April 2015

    Paclitaxel Reduced graphene oxide Graphite oxide Puri fi cation Carbon nanotube

    Graphite oxide(GO)and reduced graphene oxide(rGO)nanosheets were synthesized with a low-cost manufacturing method.The morphology and structures of the synthesized samples were studied using X-ray diffraction(XRD),atomic force microscopy(AFM),Fourier-transform infrared(FTIR)and Raman spectroscopy.The ef fi ciencies of GO and rGO as novel candidate adsorbents in the pre-puri fi cation of paclitaxel were compared and contrasted with those of commercial graphite(Gt),graphene(G)and multi-wall carbon nanotube(MWCNT).According to UV–vis and HPLC analyses,rGO was evaluated as the best absorbent for the removal of impurities in pre-puri fi cation of paclitaxel from plant cell cultures. In contrast,the GO had the poorest pro fi ciency for paclitaxel pre-puri fi cation in comparison with the other carbonaceous adsorbents.This is attributed to the existence of many localized defects in theπstructure of GO that is related to weakness ofπ–πstacking interactions between crude extract impurities and GO.

    ?2015 Xi'an Jiaotong University.Production and hosting by Elsevier B.V.All rights reserved.This is an open access article under the CC BY-NC-ND license(http://creativecommons.org/licenses/by-nc-nd/4.0/).

    1.Introduction

    Paclitaxel,as a contemporary exciting plant-derived anticancer drug,was fi rst isolated from the inner bark of the Taxus brevifolia [1].Using high performance liquid Chromatography(HPLC)is essential to obtain high level of purity and yield of this drug.However,puri fi cation by HPLC has no effective resolving power so long as the feed materials are not previously enriched for paclitaxel[2]. Pre-puri fi cation procedures before fi nal HPLC runs often requires use of some adsorbents that improve purity of crude extracts.This increases the purity and yield and decreases the cost of the fi nal paclitaxel products.

    On the other hand,graphite(Gt)is one of the naturally occurring crystalline forms of carbon used as industrial adsorbents. Carbon nanotubes(CNTs)are relatively new ef fi cient carbonaceous sorbents because of their large speci fi c surface area and hollow structure[3].Graphene(G)is a new member of the carbon family with a one-atom-thick sheet of honeycomb carbon lattice structure[4].Graphite oxide(GO)is a layered compound that can be synthesized by oxidizing graphite.The oxygenated functional groups on GO along with its large surface area indicate it can be used as an ef fi cient adsorbent[5].The chemical reduction of GO is a typical method for the production of reduced graphene oxide (rGO).However,few studies have been made for exploring the possibility of using this cost effective rGO as an adsorbent.

    In this investigation,pro fi ciencies of fi ve different carbonbased adsorbents(i.e.rGO,GO,Gt,G and CNT)were evaluated in pre-puri fi cation of paclitaxel.We focused on comparing the effectiveness and removal ability of color and impurities from crude paclitaxel extract obtained from plant cell culture,for the above mentioned adsorbents.To the best of our knowledge,this is the fi rst report to compare the adsorptive role of carbonaceous materials in pre-puri fi cation of paclitaxel.

    2.Experimental

    Natural fl ake graphite was provided by Qingdao Dingding Graphite Products Factory(Shandong,China),Graphene and multi-wall carbon nanotube were purchased from US Research Nanomaterials,Inc.(Houston,USA).GO was prepared from natural graphite using modi fi ed Hummer’s method[6].For preparation of rGO,100 mg of GO in 100 mL of water was ultrasonicated for 30 min,to which ammonia solution was added to increase the pH up to 10 and then 1 mL of hydrazine hydrate was added and the solution was heated at 100°C for 24 h.After cooling the solution, the resulting black precipitates were centrifuged and washed three times with deionized(DI)water and fi nally dried at 60°C.

    Fresh stems of Taxus baccata were collected from Botanical Garden of University of Tehran,Karaj,Iran.After sterilization,theexplants were cultured on a B5 medium and fi nally kept in a growth chamber at 24°C under dark condition[7].The pH of the medium was carefully adjusted to 5.8 prior to autoclaving.Calli cultures were transferred to a fresh B5 medium every 2 weeks[8]. Concisely,20 g of dry weight freeze-dried biomass was fi rst subjected to 800 mL of hexane at room temperature for 12 h.Then the mixture was centrifuged(5000 rpm)for 20 min and the supernatant was discarded.The pellet,in the following,was extracted with 400 mL of MeOH:CH2Cl2(1:1)by sonication for 1 h at room temperature,centrifuged at 5000 rpm for 20 min and the supernatant was transferred to the next glass tubes.The extracts were dried at 25°C under vacuum and redissolved in 200 mL of dichloromethane plus 200 mL of distilled water.Subsequent to vortexing for 10 s and centrifuging at 5000 rpm for 20 min,the organic fraction was isolated and dried under vacuum.This dark brown color dried crude extract was utilized as starting material for adsorbent treatments.

    A stock solution of 1500 mg/L extract was prepared by dissolving of dried crude in dichloromethane.Since then,certain amounts of each adsorbent(i.e.rGO,GO,Gt,G and CNT)were added separately to this extract solution in 5 mL tubes.The mixture was shaken for 45 min at 40°C and then centrifuged.During adsorption treatment, the solution turned colorless.The decolorization ef fi ciency of adsorbents was investigated using a UV–vis spectrophotometer (Shimadzu UV-2100,Kyoto,Japan).Decolorization(%)was calculated from the total absorbance of solution in the visible range(400–800 nm)of UV–vis spectrum as Eq.(1):

    where A0and Aeare the total absorbance of crude extract(from 400 to 800 nm)before and after treatment with adsorbent, respectively.

    3.Results and discussion

    3.1.Characterization of synthesized GO and rGO

    Fig.1.(A)XRD patterns of Gt along with synthesized GO and rGO.(B)AFM image of GO.

    XRD(Philips Xpert MPD,Eindhoven,Netherlands),and AFM (VEECO CP-Research,New York,USA)analyses were used to confi rm the micro-structures and morphology of GO and rGO.XRD spectra obviously showed the oxidation of graphite and preparation of GO(Fig.1A).The diffraction peak of GO appeared at 10.58° which originated from the diffraction on its(0 0 2)layer planes with the basal spacing of 0.959 nm.This was along with a broad diffraction peak at 22.29 nm which was interpreted in terms of short-range order in stacked graphene sheets[9].The XRD pattern of rGO showed the broad peak at about 25°with interlayer spacing of approximately 0.378 nm(Fig.1A).This was much smaller than the 0.959 nm for GO,and was closer to the(0 0 2)graphite peak of 0.334 nm.The sharp peak at 2θ=26.6°indicated a highly organized crystal structure with an interlayer spacing of 0.339 nm, which was consistent with the layer spacing of normal graphite. Moreover,a weak peak at 2θ=8.7°,(d-spacing of 0.768 nm)appeared in the XRD pattern of rGO which was similar to the typical diffraction peak of GO.

    AFM was used for quantifying the degree of exfoliation,thickness,and surface roughness of GO(Fig.1B).The samples were prepared by drop casting onto a silicon oxide wafer(0.05 mg/mL). AFM image revealed that isolated GO nanosheets were well exfoliated and dispersed with a thickness of about 1.5 nm for each.

    In the FTIR(Thermo spectrometer,Madison,USA)spectrum of GO(Fig.2A),the peak at 1722 cm-1corresponded to the stretching band of C=O in carboxylic acid or carbonyl moieties.The intense band at 3426 cm-1was attributed to O–H stretching.The peak at 1638 cm-1(aromatic C=C)could be assigned to the skeletal vibrations of un-oxidized graphitic domains of GO and the deformation of the C–O was observed at 1191 cm-1[10].FTIR spectrum of rGO also con fi rmed the reduction of GO,as the carboxyl peak at 1722 cm-1disappeared entirely.In addition,the O-H(1432 cm-1)and the C-O stretching peaks decreased after the reduction treatment,indicating that most oxygenated functional groups in the GO were removed.The presence of phenol C=C ring stretching(1531 cm-1)was additional proof on the reduction of GO(Fig.2B)[11].Raman spectrum(Almega Thermo Nicolet,Madison,USA)of GO displayed two characteristic peaks, the D band around 1340 cm-1and the G band at 1584 cm-1(Fig.2C).The intensity ratio of D over G band(the R-value=ID/IG) was usually used as a measure of the degree of disorder and the average size of the sp2domain which was calculated to be 0.91from the spectrum[12].The Raman spectrum of rGO also contained both G and D bands(at 1565 and 1330 cm-1,respectively), but the intensity ratio of D over G band(1.80)increased compared to that in GO(Fig.2D).Maybe this was due to a decrease in the average size of the sp2domains upon GO reduction and production of new graphitic structures[12].

    Fig.2.FTIR spectra of synthesized(A)GO and(B)rGO,Raman spectra of synthesized(C)GO and(D)rGO.

    3.2.Selection of the best adsorbent

    The removal performances of waxy compounds and plant pigments from crude paclitaxel extract,for fi ve candidate adsorbents(i.e.rGO,GO,Gt,G and CNT)were compared and contrasted,by batch sorption treatments.Table 1 summarizes the decolorization results for these adsorbents with various amounts (20 and 30 g/L)in dichloromethane as a solvent.

    The UV–vis spectra of crude extract with light brown color showed the presence of carotenoids as plant pigments which are produced from eight isoprene molecules with large delocalizedπ electron system.Considering the structural features of these pigments as adsorbates and chemical structure and functionalities of carbonaceous hydrophobic adsorbents(i.e.rGO,CNT,G and Gt), the main plausible mechanism for decolorization of the crude extract wasπ–πelectron interactions taking place betweendelocalized and conjugated electrons of adsorbent andπelectron system of carotenoids[13].However,in the case of hydrophilic GO adsorbent,oxygen functionalities in GO surfaces made many localized defects in itsπ-structure;So,the poorer ef fi ciency of GO in comparison with the other adsorbents(i.e.G,rGO and CNT)may result from more weakness ofπ–πstacking interactions between carotenoids and GO.In contrast,chemical reduction of graphene oxide can restore the graphitic network in the basal plane of rGO. Consequently,on the basis of chemistry involving the adsorption treatment,π–πstacking interactions were occurred more effectively between rGO and adsorbate which was probably the reason for superiority of rGO over GO in decolorization of taxol crude extracts,particularly in dichloremethane.

    Table 1 The effect of adsorbent treatment on decolorization and purity of crude extract from plant cell culture in two different adsorbent amounts.

    On the other hand,comparison between decolorization(%) results of rGO and commercial G and CNT displayed that in higher amounts(30 g/L)of adsorbent the decolorization ef fi ciency was almost the same for all three adsorbents,but in the lower dosages (20 g/L)the superiority of rGO over G and CNT was con fi rmed.This difference can be attributed to the availability of smaller surface area and fewer sorption sites in lower amounts of adsorbents. While,with the increasing adsorbent content,the number of available adsorption sites was expected to increase removal ef ficiency for all adsorbents.Furthermore,the purity of paclitaxel was evaluated by HPLC(Shimadzu 20AD,Kyoto,Japan),to determine the effectiveness of each adsorbent.Separation conditions involved C18column with mobile phase composition of water/acetonitrile(70:30,v/v)at fl ow rate of 1 mL/min,with an injection volume of 20μL.UV detector at wavelength of 227 nm was used for detection.Authentic paclitaxel(purity:97%)was purchased from Sigma-Aldrich and used as standard.HPLC analyses confi rmed the decolorization results and purity of paclitaxel decreased in the order of rGO(18.8%)>CNT(11.8%)>G(10.6%)>GO (8.7%)>Gt(8.8%)(Table 1).These results proved that adsorption treatments using these carbonaceous materials could be a suitable way to improve paclitaxel purity.Accordingly,treatment of crude with rGO resulted in more than four times of increase in the purity of paclitaxel from 3.9%to 18.8%.Therefore,from an economical perspective,rGO was eventually selected as the optimumadsorbent.Our fi ndings displayed promising applications of rGO, as a cost-effective nano-adsorbent,to provide a suitable vehicle toward improvement of paclitaxel pre-puri fi cation.

    Acknowledgments

    The project was fi nancially supported by Iran National Science Foundation(INSF,No.91058040).

    References

    [1]M.C.Wani,H.L.Taylor,M.E.Wall,et al.,Plant antitumor agents.VI.Isolation and structure of taxol,a novel antileukemic and antitumor agent from Taxus brevifolia,J.Am.Chem.Soc.93(1971)2325–2327.

    [2]H.R.Jang,H.J.Oh,J.H.Kim,et al.,Synthesis of mesoporous spherical silica via spray pyrolysis:pore size control and evaluation of performance in paclitaxel pre-puri fi cation,Microporous Mesoporous Mater.165(2013)219–225.

    [3]X.M.Ren,C.L.Chen,M.Nagatsu,et al.,Carbon nanotubes as adsorbents in environmental pollution management:a review,Chem.Eng.J.170(2011) 395–410.

    [4]K.S.Novoselov,A.K.Geim,S.Morozov,et al.,Electric fi eld effect in atomically thin carbon fi lms,Science 306(2004)666–669.

    [5]S.Stankovich,R.D.Piner,X.Chen,etal.,Stable aqueous dispersions ofgraphitic nanoplatelets via the reduction of exfoliated graphite oxide in the presence of poly(sodium 4-styrenesulfonate),J.Mater.Chem.16(2006)155–158.

    [6]W.S.Hummers,R.E.Offeman,Preparation of graphitic oxide,J.Am.Chem.Soc. 80(1958)1339.

    [7]O.L.Gamborg,R.A.Miller,K.Ojima,Nutrient requirements of suspension cultures of soybean root cells,Exp.Cell Res.50(1968)151–158.

    [8]N.Tapia,A.Zamilpa,M.Bon fi ll,et al.,Effect of the culture medium and biotic stimulation on taxane production in Taxus globosa Schltdl in vitro cultures, Acta Physiol.Plant.35(2013)3447–3455.

    [9]C.Nethravathi,M.Rajamathi,Chemically modi fi ed graphene sheets produced by the solvothermal reduction of colloidal dispersions of graphite oxide,Carbon 46(2008)1994–1998.

    [10]S.Stankovich,R.D.Piner,S.T.Nguyen,et al.,Synthesis and exfoliation of isocyanate-treated graphene oxide nanoplatelets,Carbon 44(2006)3342–3347.

    [11]M.El Achaby,F.Z.Arrakhiz,S.Vaudreuil,et al.,Piezoelectricβ-polymorph formation and properties enhancement in graphene oxide–PVDF nanocomposite fi lms,Appl.Surf.Sci.258(2012)7668–7677.

    [12]A.Ferrari,J.Robertson,Interpretation of Raman spectra of disordered and amorphous carbon,Phys.Rev.B 61(2000)14095–14098.

    [13]M.R.Naghavi,E.Motamedi,J.Nasiri,et al.,Evaluation of magnetic-and carbon-based nano-adsorbents application in pre-puri fi cation of paclitaxel from needles of Taxus baccata,J.Nanopart.Res.17(2015)17.

    24 January 2015

    in revised form

    ☆Peer review under responsibility of Xi'an Jiaotong University.

    .Tel.:+98 2612824809;fax:+98 2612224809.**

    .Tel.:+98 2612227609;fax:+98 2612227608.

    E-mail addresses:motamedi.elaheh@gmail.com(E.Motamedi),

    mnaghavi@ut.ac.ir(M.Reza Naghavi).

    亚洲精品一卡2卡三卡4卡5卡| 国产真实乱freesex| 热99re8久久精品国产| 伦理电影免费视频| 老司机在亚洲福利影院| 亚洲国产精品sss在线观看| 亚洲精品色激情综合| 夜夜爽天天搞| 免费在线观看黄色视频的| 最近最新中文字幕大全电影3| 欧美日韩国产亚洲二区| 婷婷精品国产亚洲av在线| 亚洲熟妇中文字幕五十中出| 69av精品久久久久久| 1024手机看黄色片| 最近最新中文字幕大全免费视频| 九色国产91popny在线| 亚洲av中文字字幕乱码综合| 亚洲欧洲精品一区二区精品久久久| 两个人看的免费小视频| 国产熟女xx| 一边摸一边做爽爽视频免费| 黄色毛片三级朝国网站| 波多野结衣巨乳人妻| 国产精品亚洲美女久久久| 好看av亚洲va欧美ⅴa在| 可以在线观看毛片的网站| 午夜日韩欧美国产| 波多野结衣巨乳人妻| 日韩国内少妇激情av| 精品不卡国产一区二区三区| 色哟哟哟哟哟哟| 动漫黄色视频在线观看| 国产av麻豆久久久久久久| 国内精品一区二区在线观看| 亚洲一区二区三区不卡视频| 欧美不卡视频在线免费观看 | 18禁国产床啪视频网站| 精品乱码久久久久久99久播| 18禁黄网站禁片免费观看直播| 成人三级黄色视频| 他把我摸到了高潮在线观看| 1024香蕉在线观看| 99re在线观看精品视频| 女生性感内裤真人,穿戴方法视频| 天天添夜夜摸| 欧美成人性av电影在线观看| 欧美乱妇无乱码| 国产成人一区二区三区免费视频网站| 精品无人区乱码1区二区| 国产人伦9x9x在线观看| 十八禁人妻一区二区| av福利片在线| 成年免费大片在线观看| 国产人伦9x9x在线观看| 一级毛片精品| 免费在线观看日本一区| 国产乱人伦免费视频| 三级男女做爰猛烈吃奶摸视频| 亚洲熟女毛片儿| 日韩大尺度精品在线看网址| 国语自产精品视频在线第100页| 亚洲成a人片在线一区二区| 日本黄大片高清| 啦啦啦观看免费观看视频高清| 国产片内射在线| cao死你这个sao货| 久久人妻av系列| 99久久99久久久精品蜜桃| 亚洲av熟女| 亚洲18禁久久av| 97碰自拍视频| 91在线观看av| 国产高清videossex| x7x7x7水蜜桃| 国产亚洲av嫩草精品影院| 舔av片在线| 免费高清视频大片| 亚洲精品久久成人aⅴ小说| 欧美日韩精品网址| 最新美女视频免费是黄的| 亚洲黑人精品在线| 黄片小视频在线播放| 亚洲自拍偷在线| 国产在线观看jvid| 国产又色又爽无遮挡免费看| 亚洲,欧美精品.| 老汉色av国产亚洲站长工具| 久久久久久大精品| 最近最新免费中文字幕在线| 男女做爰动态图高潮gif福利片| 亚洲国产欧美网| 欧美国产日韩亚洲一区| 午夜福利成人在线免费观看| 亚洲国产中文字幕在线视频| 法律面前人人平等表现在哪些方面| 99久久国产精品久久久| 97超级碰碰碰精品色视频在线观看| 狂野欧美白嫩少妇大欣赏| 很黄的视频免费| 欧美中文综合在线视频| 国产高清videossex| 日日夜夜操网爽| 亚洲一区二区三区不卡视频| 老司机深夜福利视频在线观看| 又黄又粗又硬又大视频| 全区人妻精品视频| 国产爱豆传媒在线观看 | 色播亚洲综合网| 免费在线观看完整版高清| 亚洲av美国av| 久久久久久九九精品二区国产 | 亚洲成人国产一区在线观看| 久久精品夜夜夜夜夜久久蜜豆 | 中文字幕最新亚洲高清| 成人三级做爰电影| 正在播放国产对白刺激| 啦啦啦观看免费观看视频高清| 香蕉久久夜色| 成人高潮视频无遮挡免费网站| www日本在线高清视频| 成人国产综合亚洲| 午夜视频精品福利| 国产精品综合久久久久久久免费| 12—13女人毛片做爰片一| 妹子高潮喷水视频| 亚洲色图av天堂| 亚洲国产欧美网| 看免费av毛片| www.精华液| 国产成人一区二区三区免费视频网站| 色播亚洲综合网| 一个人免费在线观看电影 | 午夜a级毛片| 在线观看一区二区三区| 成人三级黄色视频| 啦啦啦免费观看视频1| av中文乱码字幕在线| 99久久久亚洲精品蜜臀av| 白带黄色成豆腐渣| 欧美乱色亚洲激情| 可以在线观看毛片的网站| 国产成人av激情在线播放| 午夜久久久久精精品| 亚洲天堂国产精品一区在线| 成人亚洲精品av一区二区| 熟女少妇亚洲综合色aaa.| 亚洲一区高清亚洲精品| 久久久久性生活片| 三级毛片av免费| 99久久国产精品久久久| 狂野欧美白嫩少妇大欣赏| 无人区码免费观看不卡| 国产成人aa在线观看| 热99re8久久精品国产| 两人在一起打扑克的视频| 一级作爱视频免费观看| 俺也久久电影网| 久久天躁狠狠躁夜夜2o2o| 这个男人来自地球电影免费观看| 男人的好看免费观看在线视频 | 麻豆成人av在线观看| 国内少妇人妻偷人精品xxx网站 | 搡老岳熟女国产| 国产91精品成人一区二区三区| 美女高潮喷水抽搐中文字幕| 日韩 欧美 亚洲 中文字幕| 少妇人妻一区二区三区视频| 久久久久亚洲av毛片大全| 亚洲欧美日韩无卡精品| 深夜精品福利| 日本免费a在线| 又大又爽又粗| 欧美成人一区二区免费高清观看 | 午夜免费激情av| 99久久精品国产亚洲精品| 国产激情久久老熟女| 波多野结衣巨乳人妻| 国产精品一区二区三区四区免费观看 | 99热6这里只有精品| 成人三级做爰电影| 1024手机看黄色片| 国产成人啪精品午夜网站| 欧美日韩福利视频一区二区| www国产在线视频色| bbb黄色大片| 欧美色视频一区免费| 日韩有码中文字幕| 欧美日韩福利视频一区二区| 三级毛片av免费| 99热这里只有精品一区 | a级毛片a级免费在线| 18美女黄网站色大片免费观看| 国产欧美日韩一区二区精品| 国产成人aa在线观看| 制服人妻中文乱码| 久久精品国产综合久久久| 亚洲精品一卡2卡三卡4卡5卡| 国内精品一区二区在线观看| 国产精品亚洲一级av第二区| 午夜激情av网站| 女人爽到高潮嗷嗷叫在线视频| 久久久久久久久免费视频了| 久久久久精品国产欧美久久久| 国产在线精品亚洲第一网站| 亚洲av成人精品一区久久| 麻豆av在线久日| 18美女黄网站色大片免费观看| 好男人在线观看高清免费视频| 免费在线观看成人毛片| 成人亚洲精品av一区二区| 欧美久久黑人一区二区| 国产精品电影一区二区三区| 99国产精品99久久久久| 国产亚洲精品综合一区在线观看 | 草草在线视频免费看| 亚洲精品色激情综合| 一个人观看的视频www高清免费观看 | 老司机福利观看| 免费观看精品视频网站| 免费在线观看视频国产中文字幕亚洲| 欧美性长视频在线观看| 黑人巨大精品欧美一区二区mp4| 免费在线观看影片大全网站| 午夜福利18| 亚洲精品久久成人aⅴ小说| 亚洲自偷自拍图片 自拍| 成人18禁高潮啪啪吃奶动态图| 中文字幕高清在线视频| 又黄又爽又免费观看的视频| 亚洲精品中文字幕在线视频| 国产成人系列免费观看| 19禁男女啪啪无遮挡网站| 成人午夜高清在线视频| 午夜精品在线福利| 久久久久久亚洲精品国产蜜桃av| 天堂av国产一区二区熟女人妻 | 亚洲精品一区av在线观看| 久久久水蜜桃国产精品网| 午夜福利视频1000在线观看| 美女扒开内裤让男人捅视频| 亚洲国产日韩欧美精品在线观看 | 欧美成人一区二区免费高清观看 | 欧美性猛交╳xxx乱大交人| 视频区欧美日本亚洲| 国模一区二区三区四区视频 | 三级毛片av免费| 欧美久久黑人一区二区| 9191精品国产免费久久| 日本成人三级电影网站| 久久精品aⅴ一区二区三区四区| 少妇裸体淫交视频免费看高清 | 国产av麻豆久久久久久久| 久久久久久免费高清国产稀缺| 男女下面进入的视频免费午夜| 国内毛片毛片毛片毛片毛片| 国产日本99.免费观看| 99国产精品99久久久久| 日韩欧美 国产精品| 亚洲精品美女久久av网站| 一本久久中文字幕| 国产午夜精品久久久久久| 亚洲精品在线观看二区| 99re在线观看精品视频| 久久这里只有精品中国| 欧美午夜高清在线| 美女高潮喷水抽搐中文字幕| 欧美黑人巨大hd| 久久这里只有精品19| 两个人看的免费小视频| 成人高潮视频无遮挡免费网站| 村上凉子中文字幕在线| a级毛片a级免费在线| 一进一出抽搐动态| 看片在线看免费视频| 国产一级毛片七仙女欲春2| 一进一出好大好爽视频| 一边摸一边抽搐一进一小说| 美女扒开内裤让男人捅视频| 婷婷精品国产亚洲av| 日本黄大片高清| 国产精品一及| 国产成人av教育| 淫妇啪啪啪对白视频| 亚洲avbb在线观看| 国产精品亚洲av一区麻豆| 国产激情偷乱视频一区二区| 国产精品一区二区精品视频观看| 国产精品影院久久| 国产精品一及| 日韩av在线大香蕉| 女人被狂操c到高潮| 真人做人爱边吃奶动态| 欧美三级亚洲精品| 色综合亚洲欧美另类图片| 免费看美女性在线毛片视频| 最近在线观看免费完整版| 亚洲国产中文字幕在线视频| 激情在线观看视频在线高清| 亚洲精品久久成人aⅴ小说| 国产精品 国内视频| 91大片在线观看| 可以在线观看毛片的网站| 一区二区三区激情视频| 99热只有精品国产| 麻豆av在线久日| 最近最新中文字幕大全电影3| 夜夜躁狠狠躁天天躁| 国产精品久久久久久久电影 | 最近最新免费中文字幕在线| 99riav亚洲国产免费| 欧美大码av| 黄色 视频免费看| 久久香蕉国产精品| 三级毛片av免费| 亚洲国产精品久久男人天堂| 成人国产综合亚洲| 18禁观看日本| 国产成年人精品一区二区| 这个男人来自地球电影免费观看| 99久久综合精品五月天人人| 欧美日本视频| 一级a爱片免费观看的视频| www.999成人在线观看| 欧美成人性av电影在线观看| 成年免费大片在线观看| 色综合婷婷激情| 国产精品影院久久| 亚洲精品国产精品久久久不卡| 久久九九热精品免费| 久久午夜综合久久蜜桃| 国产精品99久久99久久久不卡| avwww免费| 国产黄色小视频在线观看| x7x7x7水蜜桃| 亚洲av片天天在线观看| 一区二区三区高清视频在线| 亚洲18禁久久av| 亚洲色图 男人天堂 中文字幕| 午夜精品一区二区三区免费看| 亚洲中文字幕日韩| 国产蜜桃级精品一区二区三区| 国产精品久久久久久人妻精品电影| 正在播放国产对白刺激| 欧美精品亚洲一区二区| 色噜噜av男人的天堂激情| 69av精品久久久久久| 色尼玛亚洲综合影院| 精品一区二区三区视频在线观看免费| 国产高清视频在线观看网站| 成人永久免费在线观看视频| 亚洲18禁久久av| 俺也久久电影网| 久久 成人 亚洲| 亚洲乱码一区二区免费版| 久久精品综合一区二区三区| 欧美人与性动交α欧美精品济南到| 日本一本二区三区精品| 亚洲电影在线观看av| 免费电影在线观看免费观看| 久久精品91无色码中文字幕| 蜜桃久久精品国产亚洲av| 特级一级黄色大片| 男女午夜视频在线观看| 亚洲九九香蕉| 亚洲人成伊人成综合网2020| 韩国av一区二区三区四区| 人人妻,人人澡人人爽秒播| 极品教师在线免费播放| 国产日本99.免费观看| 中文资源天堂在线| 欧美又色又爽又黄视频| 黄色视频,在线免费观看| aaaaa片日本免费| 欧美日本视频| 国产av在哪里看| 国产精品自产拍在线观看55亚洲| 在线观看免费午夜福利视频| 99国产精品99久久久久| 午夜福利高清视频| 欧美在线黄色| 麻豆国产97在线/欧美 | 首页视频小说图片口味搜索| 特级一级黄色大片| 日韩欧美三级三区| 18禁黄网站禁片午夜丰满| 老司机深夜福利视频在线观看| 色综合亚洲欧美另类图片| 国产真实乱freesex| 亚洲欧美日韩东京热| 亚洲成人国产一区在线观看| 在线观看日韩欧美| 一本精品99久久精品77| 日韩欧美 国产精品| 视频区欧美日本亚洲| 18禁美女被吸乳视频| 两个人看的免费小视频| 999精品在线视频| 亚洲av电影在线进入| 校园春色视频在线观看| 我的老师免费观看完整版| av在线天堂中文字幕| 亚洲第一电影网av| 午夜福利高清视频| 老鸭窝网址在线观看| 一级毛片高清免费大全| 色噜噜av男人的天堂激情| 在线观看免费午夜福利视频| 国内精品一区二区在线观看| 99在线人妻在线中文字幕| 国产日本99.免费观看| 欧美性长视频在线观看| 国产高清激情床上av| 日本 欧美在线| 亚洲第一电影网av| 每晚都被弄得嗷嗷叫到高潮| 亚洲九九香蕉| 久久国产精品人妻蜜桃| 最好的美女福利视频网| 久久精品91无色码中文字幕| 日本在线视频免费播放| 黄色成人免费大全| 久久久精品欧美日韩精品| 亚洲第一电影网av| av天堂在线播放| 麻豆av在线久日| 国产免费男女视频| 黄片小视频在线播放| 国产亚洲欧美98| 麻豆久久精品国产亚洲av| 18禁美女被吸乳视频| 国产黄a三级三级三级人| 99热6这里只有精品| 身体一侧抽搐| 亚洲av熟女| 黄色毛片三级朝国网站| 最近视频中文字幕2019在线8| 男女视频在线观看网站免费 | 亚洲专区字幕在线| 日韩欧美三级三区| 国产69精品久久久久777片 | 婷婷精品国产亚洲av| 露出奶头的视频| 最新美女视频免费是黄的| 97人妻精品一区二区三区麻豆| 男人的好看免费观看在线视频 | 久久久国产精品麻豆| 制服人妻中文乱码| 色在线成人网| 99在线视频只有这里精品首页| 国产精品99久久99久久久不卡| 亚洲中文av在线| 国产在线精品亚洲第一网站| 一进一出好大好爽视频| 欧洲精品卡2卡3卡4卡5卡区| 亚洲国产精品999在线| 麻豆成人午夜福利视频| 欧美日韩黄片免| 啪啪无遮挡十八禁网站| 国产成人精品久久二区二区免费| avwww免费| 欧美乱妇无乱码| 小说图片视频综合网站| 亚洲九九香蕉| 丰满人妻熟妇乱又伦精品不卡| 男人舔奶头视频| 夜夜爽天天搞| 国产激情欧美一区二区| 国产真人三级小视频在线观看| 欧美人与性动交α欧美精品济南到| 成人高潮视频无遮挡免费网站| 亚洲熟妇熟女久久| 亚洲第一欧美日韩一区二区三区| 身体一侧抽搐| 午夜免费成人在线视频| av超薄肉色丝袜交足视频| 精品国产乱子伦一区二区三区| 男女午夜视频在线观看| 欧美色视频一区免费| 午夜两性在线视频| 精品久久久久久久末码| 国产亚洲精品综合一区在线观看 | www.精华液| 人人妻人人澡欧美一区二区| 久久天躁狠狠躁夜夜2o2o| 国产成人精品久久二区二区免费| 香蕉av资源在线| 99热这里只有精品一区 | 欧美久久黑人一区二区| 神马国产精品三级电影在线观看 | 日韩精品中文字幕看吧| 一个人免费在线观看的高清视频| 夜夜躁狠狠躁天天躁| 久久精品aⅴ一区二区三区四区| 99在线视频只有这里精品首页| 黑人巨大精品欧美一区二区mp4| 国产亚洲精品久久久久5区| 日日摸夜夜添夜夜添小说| 久久天堂一区二区三区四区| 成熟少妇高潮喷水视频| www.自偷自拍.com| 男女视频在线观看网站免费 | 在线免费观看的www视频| 精品一区二区三区四区五区乱码| 精品不卡国产一区二区三区| 丝袜美腿诱惑在线| 亚洲在线自拍视频| 午夜福利欧美成人| 非洲黑人性xxxx精品又粗又长| 精品不卡国产一区二区三区| 免费观看人在逋| 国产1区2区3区精品| 香蕉av资源在线| 久久久久国产一级毛片高清牌| 午夜福利高清视频| 18禁裸乳无遮挡免费网站照片| 成人高潮视频无遮挡免费网站| 欧美一区二区国产精品久久精品 | 757午夜福利合集在线观看| 哪里可以看免费的av片| 国内久久婷婷六月综合欲色啪| 亚洲乱码一区二区免费版| 久久久国产成人免费| 黄色成人免费大全| 欧美日韩乱码在线| 黄色毛片三级朝国网站| 美女高潮喷水抽搐中文字幕| 精品久久久久久成人av| 久久久国产欧美日韩av| av福利片在线| 亚洲精品在线美女| a在线观看视频网站| 成人国产综合亚洲| 日本a在线网址| 亚洲国产欧美网| 国产精品一区二区三区四区久久| 欧美国产日韩亚洲一区| 午夜a级毛片| 人妻久久中文字幕网| 美女免费视频网站| 国产精品亚洲av一区麻豆| 最好的美女福利视频网| 老司机午夜十八禁免费视频| 又粗又爽又猛毛片免费看| 国产成人aa在线观看| 久久久久久九九精品二区国产 | 又紧又爽又黄一区二区| 国模一区二区三区四区视频 | 激情在线观看视频在线高清| 我要搜黄色片| 亚洲av成人一区二区三| 19禁男女啪啪无遮挡网站| 91老司机精品| 亚洲男人天堂网一区| 欧美久久黑人一区二区| 久久中文看片网| 精品第一国产精品| 深夜精品福利| 免费在线观看日本一区| 1024手机看黄色片| 日本黄色视频三级网站网址| 别揉我奶头~嗯~啊~动态视频| 亚洲 国产 在线| 国产97色在线日韩免费| 精品久久久久久,| 首页视频小说图片口味搜索| 精品久久久久久,| 国产成人欧美在线观看| 国产男靠女视频免费网站| 两人在一起打扑克的视频| 村上凉子中文字幕在线| 狂野欧美激情性xxxx| 啦啦啦免费观看视频1| 色综合欧美亚洲国产小说| 亚洲国产看品久久| www.精华液| 午夜久久久久精精品| 在线永久观看黄色视频| 午夜久久久久精精品| 一进一出好大好爽视频| 99热这里只有是精品50| 亚洲18禁久久av| 丁香六月欧美| 亚洲狠狠婷婷综合久久图片| 一本综合久久免费| 欧美成人性av电影在线观看| 亚洲色图av天堂| 日韩高清综合在线| 亚洲成人免费电影在线观看| 给我免费播放毛片高清在线观看| 人妻夜夜爽99麻豆av| 黄色片一级片一级黄色片| 精品久久久久久,| 国产成人欧美在线观看| av天堂在线播放| 国产成人aa在线观看| av中文乱码字幕在线| 成年免费大片在线观看| 日韩精品免费视频一区二区三区| 色av中文字幕| 亚洲激情在线av| 高潮久久久久久久久久久不卡| 国产精品一及| 脱女人内裤的视频| 国产一区二区在线av高清观看| 看免费av毛片| 亚洲精品美女久久av网站| 麻豆一二三区av精品| 亚洲av日韩精品久久久久久密| 国产激情偷乱视频一区二区| a级毛片a级免费在线| 亚洲一区二区三区不卡视频| 日日干狠狠操夜夜爽| 国产黄片美女视频| 午夜免费激情av|