• <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 ?

    Effect of Dietary Olaquindox on the Growth of Large Yellow Croaker(Pseudosciaena crocea R.)and the Distribution of Its Residues in Fish Tissues

    2014-04-17 02:43:06LIHuitaoWANGWeifangMAIKangsenAIQinghuiZHANGChunxiaoandZHANGLu
    Journal of Ocean University of China 2014年5期

    LI Huitao,WANG Weifang,MAI Kangsen,AI Qinghui,,ZHANG Chunxiao,and ZHANG Lu

    1) Key Laboratory of Mariculture of Ministry of Education, Ocean University of China,Qingdao 266003, P.R.China

    2) Qingdao Key Laboratory for Marine Fish Breeding and Biotechnology, Yellow Sea Fisheries Research Institute, Chinese Academy of Fishery Sciences, Qingdao 266071, P.R.China

    3) Fisheries College, Jimei University, Xiamen 361021, P.R.China

    ? Ocean University of China,Science Press and Spring-Verlag Berlin Heidelberg 2014

    1 Introduction

    Olaquindox(OLA),N-(2-hydroxyethyl)-3-methyl-2-quinoxalincarboxamide-1,4-dioxide,one of quinoxaline-N,N-dioxides,has been put under ban.However it was used as a medicinal feed additive early; it promotes the growth of livestock and prevents them from dysentery and bacterial enteritis(Baarset al.,1988; Anon,1989).In 1980s,OLA was used in fish and shrimp farming(Xuet al.,1988; Yeet al.,1992).Unfortunately,it was cognized gradually that OLA is toxic to fish(Caoet al.,2001; Wanget al.,2004; Yanget al.,2005),thus been put under ban by many countries including China.However,its illegal use has never completely disappeared worldwide.

    As was documented by the joint FAO/WHO Expert Committee on Food Additives,OLA is almost completely absorbable in the gastrointestinal tract of rat,dog and pig,and histological wide in distribution.The most of OLA is eliminated through urine and less through feces and by expiration.In urine,the original OLA accounts for 70%,while others include approximately 16 metabolites,of them 6 major metabolites have been fully characterized.MQCA is the main persistent residue of OLA in the edible tissues,thus is considered to be a marker of OLA in animals(FAO/WHO,1995; MOA,2002).To date,no study has been carried out on the histological distribution of OLA residue and its metabolites in fish.OLA may induce genotoxicity as was found in human hepatoma G2(HepG2)cells(Zouet al.,2011)and cause phototoxicity to human(WHO,1991; Emmertet al.,2007).We believe that OLA residue and its metabolites in fish tissues may affect human health.

    Large yellow croaker(Pseudosciaena crocea)is one of the commercially important marine fish species in China,which has been widely cultured in recent years.Early studies in this fish species focused mainly on its nutrient requirement and feed modification(Duanet al.,2001; Maiet al.,2006; Aiet al.,2007; Liet al.,2007).In this study,the effect of dietary OLA on the growth of large yellow croaker and its histological residue were determined with an emphasis on OLA and its metabolite MQCA.

    2 Materials and Methods

    2.1 Diet Preparation

    Four diets were formulated to contain 0(control,Diet 1),42.5(Diet 2),89.5(Diet 3)and 277.2(Diet 4)mg kg?1OLA with 1% OLA premix(Animal Disease Control Center,Qingdao,China)(Table 1).The protein and lipid content of these diets was about 44% and 11%,respectively,which are considered sufficient to support optimal growth of large yellow croaker(Duanet al.,2001).

    Table 1 Formulation of experimental diets(dry weight basis)

    To prepare the diets,the solid ingredients were grounded into fine powder,sieved through a 320-μm mesh and mixed thoroughly with menhaden fish oil.The mixture was made into stiff dough by adding water and then pelleted with an experimental feed mill(F-26 II,South China University of Technology,China).The pellets were dried in a ventilated oven at 60℃ for about 12 h,broken up and sieved.The prepared diets were 1.5 mm× 2.0 mm in size,which were sealed in plastic bags and stored at ?15℃.

    2.2 Feeding Trial

    Large yellow croaker juveniles were obtained from a commercial hatchery and stocked in a floating sea cage(3.0 m × 3.0 m × 3.0 m)in Xihu Bay,Ningbo,China,for 2 weeks.The fish were fed with Diet 1 during the acclimation.

    The fish were fasted for 24 h and weighed after being anesthetized with eugenol(1:10000; Shanghai Reagent Corp,China).Fish in similar size(9.75 g ± 0.35 g)were divided into 12 sea cages(1.0 m × 1.0 m × 1.5 m),3 cages each diet and 100 individuals each cage,and fed to satiation twice a day at 05:00 am and 17:00 pm,respectively,for 8 weeks.During feeding trial,water temperature and salinity were maintained at 26.5–32.5℃ and 25.0–28.0 g L?1,respectively,while dissolved oxygen was kept above 7 mg L?1.The natural light rhythm was followed throughout the trial.

    2.3 Sampling and Content Assaying

    2.3.1 Sampling

    The fish were fasted for 24 h ahead of harvest.Total number of fish in each cage was counted and their body weights were measured.Twenty fish per cage were randomly collected and stored frozen at ?20℃ to determine whole-body proximate composition and the content of OLA and its metabolite.The skin,liver and muscle were sampled under caliginous light carefully and freeze-dried in ALPHA 1-2,a freeze dryer(Martin Christ,Germany)for 24 h,then immediately stored frozen at ?20℃.

    2.3.2 Analysis of ingredients,diets and fish body composition

    Analyses of ingredients,diets and fish body composition were made following the usual procedures(AOAC,1995):samples were dried to a constant weight at 105℃ to determine the dry matter content; crude protein was determined by measuring nitrogen(N × 6.25)using the Kjeldahl method; crude lipid was measured by ether extraction using Soxhlet method; ash by combustion at 550℃ for 16 h.

    The content of OLA and MQCA was determined with a liquid chromatography(LC)equipped with ultraviolet(UV)detector set at 260 nm and 320 nm,respectively.

    2.3.3 Content assaying

    For content determination,the skin,liver and muscle were homogenized with 5 mL saturated ammonium sulfate,and then 10 mL mixed solution of acetonitrile-ethyl acetate(3:2)was added to homogenize for 1–2 min following with a 10-min centrifugation at 4200 r min?1.The supernatant were evaporated to dryness under a stream of nitrogen(Organomation Associates,Berlin,MA,USA)at 50℃water-bath.The residue were dissolved with 2 mL acetonitrile and degreased with 3 mL n-hexane for twice and centrifuged.The stock solution were evaporated to dryness under a stream of nitrogen at a water bath of 50℃and 0.5 mL methanol was added following a 1–2 min shaking mixture and centrifugation,of which 10 μL supernatant was injected into the liquid chromatography(LC)equipped with ultraviolet(UV)detector set at 260 nm to determine the concentration of OLA.The skin,liver and muscle were hydrolyzed by 5 mL 3 mol L?1NaOH at a 95?100℃ water bath for 40–45 min.The alkaline hydrolysate was acidified to pH≤1 with 3 mL HCl and extracted with 15 mL ethyl acetate following with a 10-min centrifugation at 4200 r min?1.The supernatant was washed with 5 mL distilled water by shaking to clarify and rejecting the lower water phase twice.Then 5 mL 0.5 mol L?1citric acid buffer(pH 6.0)was added into the extraction and mixed to get the lower buffer phase.Then,the aqueous extraction was acidified with 3 mL HCl.The acidified aqueous extraction was transferred into a cation exchange column(AG MP-50 resin)for ion-exclusion chromatography.The column was washed with 50 mL 1 mol L?1HCl and 70 mL mixed solution of methanol with water(50 + 50)to collect the eluate,respectively.The eluate was extracted with 25 mL CHCl3triplicate after adding 2 mL HCl and rotary evaporated to dryness at 45–50℃.The residue were dissolved with 2 mL methanol twice and evaporated to dryness under a stream of nitrogen at a water bath of 50℃,then 0.5 mL methanol was added following a 1–2 min shaking mixture and centrifugation,of which 10 μL supernatant was injected into the liquid chromatography(LC)equipped with ultraviolet(UV)detector set at 320 nm to determine the concentration of MQCA.

    2.4 Data Processing

    The weight gain rate(WGR)of fish was determined with the equation whereWtandWoare final and initial mean body weight of fish,respectively.Data corresponding to each diet were subjected to one-way ANOVA with SPSS 10.0 for windows.When overall difference was significant(P< 0.05),Tukey’s test was used to compare the means between diets(Zar,1984).

    3 Results

    3.1 Survival and Growth

    Fish fed the diet with 277.2 mg kg?1OLA were slow in feed intaking and nervous to any stimulation(e.g.,mad jumping).Occasionally,hyperemia and hemorrhage were observed at the base of fins and the corner of the mouth and in abdomen.The survival rate ranged from 86.0% to 92.0% was significantly influenced by dietary treatment(Table 2).Fish fed diet with 42.5 and 89.5 mg kg?1OLA survived significantly higher than those fed with control diet and 277.2 mg kg?1OLA diet(P< 0.05); while fish fed diet with 277.2 mg kg?1OLA had a significantly lower survival rate than the control)(P< 0.05).The WGR of fish was significantly influenced by the dietary OLA.Fish fed diets with 42.5 and 89.5 mg kg?1OLA had signifycantly higher WGR(173.0% and 184.0%,respectively)than control(133.3%)(P< 0.05),and the fish fed with control diet and 277.2 mg kg?1OLA diet had similar WGR(Table 2).

    Table 2 Survival and growth performance of large yellow croaker

    3.2 Body Composition

    The dietary OLA did not significantly influence the composition of fish body.Water(69.2%–70.3%),lipid(8.1%–8.7%)and ash(4.1%–4.3%)content was within a normal range(Table 3).Although body protein content(18.4%)was higher in fish fed diet with 89.5 mg kg?1OLA than that of control(16.5%)(P< 0.05),but such a difference was not significant among other dietary OLA treatments(P> 0.05)(Table 2).

    Table 3 Effect of dietary olaquindox on the body composition(% wet weight)of large yellow croaker

    3.3 Histological Distribution OLA and MQCA

    OLA and MQCA were not detectable in the fish tissues of control group; however,OLA residue and its metabolite MQCA significantly increased in skin,liver and muscle in a dose-dependent pattern(P< 0.05).Fish fed diet with 277.2 mg kg?1OLA had significantly higher OLA and MQCA in their liver(3.44 and 0.39 mg kg?1,respectively),skin(0.46 and 0.09 mg kg?1,respectively)and muscle(0.24 and 0.06 mg kg?1,respectively)than those fed other diets.In average,fish fed diet with 42.5,89.5 and 277.2 mg kg?1OLA had the highest content of OLA and MQCA in their liver followed by skin and muscle(Table 4).

    Table 4 Content of OLA and MQCA in different tissues of large yellow croaker

    4 Discussion

    OLA is a synthetic antimicrobial chemical,which can promote the growth of animals and prevent them from the infection of pathogens.In this study,we found that the survival rate of large yellow croaker was significantly influenced by dietary OLA,indicating that OLA played a role as an antimicrobial agent.However,such a scenario was not appeared when dietary OLA increased to 277.2 mg kg?1,of which the survival rate was lower than that of control.A similar trend was also reported early in grass carp(Yeet al.1992).We believed that the toxicity of OLA(Caoet al.,2001; Wanget al.,2004; Yanget al.,2005),especially when its content is high,caused such a pattern of the influence of OLA on the survival rate of fish.

    It is believed that OLA can inhibit the growth of harmful bacteria and influence the metabolism of body nutrients,thus promoting the synthesis of nutrients,especially protein,of animal(Yeet al.,1992; Shenet al.,1995).In this study,the content of protein of the fish fed diet with 42.5 mg kg?1OLA was significantly higher than that of control,which may be explained by these early understandings.Nevertheless,high content of OLA may disrupt such a scenario; the fish fed diet with 277.2 mg kg?1OLA has lower content of protein than control.

    The residue of OLA and its metabolites have been documented early(WHO,1991; FAO,1991).As reported early,70% of OLA administrated orally may be eliminated through urine unchanged,and 16 metabolites of OLA have been detected in the urine,of which 6 major metabolites are fully characterized(WHO,1991).Among the metabolites of OLA,MQCA was the last major remaining detectable metabolite in animal,has been designated as the marker substance(FAO/WHO,1995; MOA,2002).In this study,OLA and MQCA were high in content in the tissues of fish fed diet with 42.5,89.5 and 277.2 mg kg?1OLA but not in control,demonstrating that OLA and MQCA accumulated in the tissues of large yellow croaker.The content of OLA in diet significantly affected the histological concentration of its residue and its metabolite MQCA(P< 0.05),and showed an obvious dose-dependent relationship with the residues in tissues.A similar finding was also reported in mirror carp(Yeet al.,2003)and pig(Zhanget al.,2011a).The distribution of OLA and its metabolite MQCA was histologically different.In average,the content of OLA and MQCA was the highest in liver which was followed by that in skin and muscle.This pattern was similar to the report early in carp(Wanget al.,2003; Yeet al.,2003; Liet al.,2012)and tilapia(Chenet al.,2011).The metabolism pathway of OLA in animals may explain such a pattern.First,the liver is the major metabolizing places for OLA(WHO,1991),in which more OLA is transformed than in skin and muscle.Second,liver damage and metabolic disorder caused by OLA may slow the elimination of residues in liver(Zenget al.,1995; Yanget al.,2005).These factors may explain why the content of residual OLA and its metabolite MQCA in liver is the highest.

    The toxicity of OLA and their metabolites to fish have been documented intensively,which included cumulative toxicity(Wanget al.,2004; Yanget al.,2005),photosensitive toxicity(De Vrieset al.,1990)and genotoxity(WHO,1991; Caoet al.,2001; Zouet al.,2011; Zhanget al.,2011b; Zhaoet al.,2013).Despite OLA has been put under ban in many countries,its illegal use in aquaculture has never vanished from sight all over the world.In this study,we found that OLA residue and its metabolite MQCA were detectable in diverse tissues of large yellow croaker when it was fed with the diet containing OLA.The OLA residue and its metabolites in farmed large yellow croaker is a potential risk to human health,thus we should keep watch on its use in order to ensure the safety of our food.

    Acknowledgements

    This study was supported by the National Key Technologies R & D Program for the 10thand 11thFive-year Plan of China(2001BA505B-06; 2006BAD03B03)and the Program for Changjiang Scholars and Innovative Research Team in University.We thank Liufu Z.G.and Liu X.W.for their assistance in diet preparation,and Wang Z.L.,Chen J.H.,Shentu J.K.,and Tan F.P.for their assistance in laboratory work.

    Ai,Q.,Mai,K.,Zhang,L.,Tan,B.,Zhang,W.,Xu,W.,and Li,H.,2007.Effects of dietary β-1,3 glucan on innate immune response of large yellow croaker,Pseudosciaena crocea.Fish and Shellfish Immunology,22:394-402.

    Anon,1989.Compendium of data sheets for veterinary products.In:National Office of Animal Health.Datapharm Publications Ltd,London,90pp.

    Association of Official Analytical Chemists(AOAC),1995.Official Methods of Analysis of the Association of Official Analytical Chemists.16th edition.Arlington,VA,1-45.

    Baars,A.J.,Van der Molen,E.J.,Spierenburg,T.J.,DE Graaf,G.J.,Nabuurs,J.J.A.,and Jager,L.P.,1988.Comparative toxicity of three quinoxaline-di-N-dioxide feed additives in young pigs.Archives Toxicology, 12(Suppl):405-409.

    Cao,S.Z.,Zhang,L.,Liang,J.P.,and Liu,Z.P.,2001.Progress of study on the special toxicology of quinoxaline-1,4-dioxide-type antibacterial and growth-promoting agents.Progress in Veterinary Medicine,22:17-20(in Chinese with English abstract).

    Chen,Y.,Lin,L.,Zhang,S.,Li,C.,and Li,Z.,2011.Pharmacokinetics of olaquindox and its metabolite in tilapia fish.Progress in Veterinary Medicine,32(10):54-58(in Chinese with English abstract).

    De Vries,H.,Bojarski,J.,Donker,A.A.,Bakri,A.,and Beyersbergen van Henegouwen,G.M.,1990.Photochemical reactions of quindoxin,olaquindox,carbadox and cyadox with protein,indicating photoallergic properties.Toxicology,63(1):85-95.

    Duan,Q.,Mai,K.,Zhong,H.,Si,L.,and Wang,X.,2001.Studies on the nutrition of the large yellow croaker,Pseudosciaena croceaR.I:Growth response to graded levels of dietary protein and lipid.Aquaculture Research,32(Suppl 1):46-52.

    Emmert,B.,Schauder,S.,Palm,H.,Hallier,E.,and Emmert,S.,2007.Disabling work related persistent photosensitivity following photoallergic contact dermatitis from chlorpromazine and olaquindox in a pig breeder.Annals of Agricultural and Environmental Medicine,14:329-333.

    FAO/WHO,Joint Expert Committee on Food Additives,1995.Evaluation of certain veterinary drug residues in food.WHO Technical Report Series,851:19.

    Food and Agriculture Organization of the United Nations(FAO),1991.Residues of some veterinary drugs in animals and foods.FAO Food and Nutrition Paper.Food and Agriculture Organization,Rome,41/3:85-96.

    Li,H.,Mai,K.,Ai,Q.,Zhang,C.,and Zhang,L.,2009.Effects of dietary squid viscera meal on growth and cadmium accumulation in tissues of large yellow croaker,Pseudosciaena croceaR.Frontiers of Agriculture in China,3(1):78-83.

    Li,H.,Mai,K.,Ai,Q.,Zhang,L.,Zhang,C.,Zhang,W.,and Liufu,Z.,2007.Apparent digestibility of selected protein ingredients for larger yellow croakerPseudosciaena crocea.Acta Hydrobiologica Sinica,31(3):80-86(in Chinese with English abstract).

    Li,S.,Ha,X.,and Mao,H.,2012.Study on the residual rules of olaquindox in carp.Journal of Anhui Agricultural Sciences,40(30):14746-14747(in Chinese with English abstract).

    Mai,K.,Zhang,C.,Ai,Q.,Duan,Q.,Xu,W.,Zhang,L.,Liufu,Z.,and Tan,B.,2006.Dietary phosphorus requirement of large yellow croaker,Pseudosciaena croceaR.Aquaculture,251:346-353.

    MOA(Ministry of Agriculture of China),2002.Maximum residue limits of veterinary drugs in the foods of animal.Announcement No.235,Annex 2:20.

    Shen,W.,Zhang,Z.,and Cai,H.,1995.A preliminary study on the effects of the diets with olaquindox on growth rate of fingerling bluntnose black bream.Cereal and Feed Industry,4:23-24(in Chinese with English abstract).

    Wang,K.,Geng,Y.,and Liu,K.,2004.Study on cumulative toxicity of OLA in common carp.Journal of Sichuan Agricultural University,22:183-186(in Chinese with English abstract).

    Wang,K.,Geng,Y.,Ye,S.,and Huang,X.,2003.Studies on pathology and tissue concentration of the chronic olaquindox poisoning inCyprinus carpio.Journal of Fisheries of China,27(1):75-82(in Chinese with English abstract).

    WHO,1991.Toxicological evaluation of certain veterinary drug residues in food.WHO Food Additive Series 27.World Health Organization,Geneva,227pp.

    Xu,J.,Li,A.,Lou,W.,and Lu,D.,1988.The effects of promoter

    on the promoting growth ofPenaeus orientalis kishinouye.

    Marine Sciencies,5:35-39(in Chinese with English abstract).

    Yang,X.L.,Hu,K.,Qiu,J.Q.,and Diao,J.H.,2005.Studies on accumulation and toxic of olaquindox in fishes.Acta Hydrobiologica Sinica,29:13-19(in Chinese with English abstract).

    Ye,J.,Chen,Y.,and Shen,Z.,1992.Effect of HMQ supplemental concentration on the growth and survival rate of grass carp.Journal of Zhejiang College of Fisheries,11(1):25-31(in Chinese with English abstract).

    Ye,J.,Yang,Y.,Lu,T.,Liu,H.,Zhao,J.,Han,Y.,and Li,H.,

    2003.The accumulation and elimination of olaquindox in tissues of mirror carp.Journal of North East Forestry University,31(3):53-56(in Chinese with English abstract).

    Zar,J.H.,1984.Production.In:Biostatistical Analysis.Zar,J.H.,ed.,Prentice-Hall,Englewood Cliffs,NJ,293-305.

    Zeng,Z.L.,Dong,L.B.,and Chen,Z.L.,1995.Studies on elimination and residues of olaquindox in chicken tissues.Acta Veterinaria et Zootechnica Sinica,26:327-333(in Chinese with English abstract).

    Zhang,J.,Zeng,Z.,and Ge,C.,2011a.Analysis on the distribution and correlation of residues of olaquindox in animal plasma and tissue.China Animal Health,5:13-15(in Chinese with English abstract).

    Zhang,T.,Tang,S.,Jin,X.,Liu,F.,Zhang,C.,Zhao,W.,Zhang,S.,Sun,C.,and Xiao,X.,2011b.c-Myc influences olaquindox-induced apoptosis in human hepatoma G2 cells.Molecular and Cellular Biochemistry,354:253-261.

    Zhao,W.,Tang,S.,Jin,X.,Zhang,C.,Zhang,T.,Wang,C.,Sun,Y.,and Xiao,X.,2013.Olaquindox-induced apoptosis is suppressed through p38 MAPK and ROS-mediated JNK pathways in HepG2 cells.Cell Biology and Toxicology,29:229-238.

    Zou,J.,Chen,Q.,Jin,X.,Tang,S.,Chen,K.,Zhang,T.,and Xiao,X.,2011.Olaquindox induces apoptosis through the mitochondrial pathway in HepG2 cells.Toxicology,285:104-113.

    亚洲中文日韩欧美视频| 毛片女人毛片| 国产精品 国内视频| 午夜精品在线福利| 毛片女人毛片| 可以免费在线观看a视频的电影网站| 精品日产1卡2卡| 欧美色视频一区免费| 麻豆国产av国片精品| 香蕉丝袜av| 露出奶头的视频| 欧美黑人欧美精品刺激| 变态另类丝袜制服| 成在线人永久免费视频| 国产黄a三级三级三级人| 欧美一区二区国产精品久久精品 | 中文字幕人成人乱码亚洲影| av在线播放免费不卡| 亚洲精品久久成人aⅴ小说| 国产欧美日韩一区二区三| 国产精品一及| 国产午夜精品久久久久久| 亚洲av电影在线进入| 成人午夜高清在线视频| 免费搜索国产男女视频| 国产精品av久久久久免费| 美女黄网站色视频| 黄色女人牲交| 久久精品aⅴ一区二区三区四区| 国产高清视频在线播放一区| 久久人人精品亚洲av| 亚洲国产精品999在线| 国产精品久久久久久久电影 | 久久午夜亚洲精品久久| 嫁个100分男人电影在线观看| 亚洲色图 男人天堂 中文字幕| 狂野欧美白嫩少妇大欣赏| 日本一二三区视频观看| 嫁个100分男人电影在线观看| 十八禁人妻一区二区| 成人手机av| 午夜福利在线观看吧| 香蕉国产在线看| 久久久久性生活片| 久久久国产成人精品二区| 三级毛片av免费| 欧美成人免费av一区二区三区| 国产成人av激情在线播放| 50天的宝宝边吃奶边哭怎么回事| 黄色a级毛片大全视频| 在线国产一区二区在线| 色老头精品视频在线观看| 在线a可以看的网站| 亚洲精品中文字幕在线视频| 在线视频色国产色| ponron亚洲| 男人舔女人下体高潮全视频| 色综合站精品国产| 一边摸一边抽搐一进一小说| aaaaa片日本免费| 精品日产1卡2卡| 夜夜躁狠狠躁天天躁| 两人在一起打扑克的视频| 老司机午夜福利在线观看视频| 性欧美人与动物交配| 在线看三级毛片| 黄片小视频在线播放| www.999成人在线观看| 国产一区二区在线av高清观看| 国产亚洲精品久久久久5区| 亚洲五月婷婷丁香| 欧美丝袜亚洲另类 | 这个男人来自地球电影免费观看| 亚洲人与动物交配视频| 校园春色视频在线观看| 国产激情偷乱视频一区二区| 国产午夜精品论理片| 日本黄色视频三级网站网址| 欧美日本亚洲视频在线播放| 丰满人妻一区二区三区视频av | 99久久久亚洲精品蜜臀av| 少妇熟女aⅴ在线视频| 亚洲午夜精品一区,二区,三区| 我的老师免费观看完整版| 国产三级中文精品| 欧美午夜高清在线| 亚洲av电影在线进入| 久久天躁狠狠躁夜夜2o2o| 亚洲人与动物交配视频| 国内久久婷婷六月综合欲色啪| 中文字幕高清在线视频| 国产亚洲av高清不卡| 又粗又爽又猛毛片免费看| 免费av毛片视频| 一个人免费在线观看电影 | 很黄的视频免费| 最新在线观看一区二区三区| 国产区一区二久久| 久久伊人香网站| 亚洲午夜理论影院| 精品不卡国产一区二区三区| 欧美av亚洲av综合av国产av| 嫩草影院精品99| 99久久无色码亚洲精品果冻| 免费观看精品视频网站| 国产精品久久久久久亚洲av鲁大| 夜夜爽天天搞| 可以在线观看毛片的网站| 日韩精品青青久久久久久| 我要搜黄色片| 国产精品一区二区免费欧美| 91字幕亚洲| 国内毛片毛片毛片毛片毛片| 女警被强在线播放| 亚洲最大成人中文| 亚洲美女视频黄频| 国产真实乱freesex| 午夜日韩欧美国产| 国产免费av片在线观看野外av| 黄片大片在线免费观看| 91在线观看av| 免费av毛片视频| 国产欧美日韩一区二区精品| 老司机深夜福利视频在线观看| 美女免费视频网站| 免费搜索国产男女视频| 国产av麻豆久久久久久久| 国产精品影院久久| 两个人视频免费观看高清| 99热这里只有精品一区 | 亚洲精品在线观看二区| 99久久99久久久精品蜜桃| 一本综合久久免费| 12—13女人毛片做爰片一| 国产精品香港三级国产av潘金莲| 欧美性猛交黑人性爽| 亚洲精华国产精华精| 老司机午夜福利在线观看视频| 亚洲av成人一区二区三| 99国产精品一区二区三区| 亚洲精品久久成人aⅴ小说| 成人手机av| 色综合婷婷激情| av国产免费在线观看| 丝袜人妻中文字幕| 搡老熟女国产l中国老女人| 99re在线观看精品视频| 久久九九热精品免费| 啦啦啦韩国在线观看视频| 欧美又色又爽又黄视频| 免费看十八禁软件| 欧美日本视频| 岛国视频午夜一区免费看| 国产精品美女特级片免费视频播放器 | 91麻豆av在线| 黄色 视频免费看| 极品教师在线免费播放| 久久热在线av| 国产在线观看jvid| 亚洲人成电影免费在线| 777久久人妻少妇嫩草av网站| 99精品欧美一区二区三区四区| 精品无人区乱码1区二区| 亚洲午夜精品一区,二区,三区| 亚洲成人国产一区在线观看| 国产精品亚洲av一区麻豆| 无限看片的www在线观看| 麻豆久久精品国产亚洲av| av国产免费在线观看| 亚洲无线在线观看| 国产成人影院久久av| 国产单亲对白刺激| 精品国内亚洲2022精品成人| 久久香蕉精品热| av国产免费在线观看| 91成年电影在线观看| 亚洲成av人片免费观看| 精品久久久久久久久久久久久| 亚洲av中文字字幕乱码综合| 国产精品亚洲一级av第二区| 午夜影院日韩av| 视频区欧美日本亚洲| 国产精品美女特级片免费视频播放器 | 亚洲欧美日韩高清专用| xxxwww97欧美| 亚洲,欧美精品.| 舔av片在线| 精品无人区乱码1区二区| 成人精品一区二区免费| 国产精品亚洲美女久久久| 久久久久久九九精品二区国产 | 99热6这里只有精品| 精品一区二区三区四区五区乱码| 99精品久久久久人妻精品| 久久精品国产亚洲av香蕉五月| 免费高清视频大片| 夜夜爽天天搞| 欧洲精品卡2卡3卡4卡5卡区| www日本在线高清视频| 久久久国产欧美日韩av| 亚洲国产欧美人成| 99久久精品国产亚洲精品| 国内精品一区二区在线观看| 久久久国产精品麻豆| 国产激情久久老熟女| 午夜视频精品福利| 亚洲五月婷婷丁香| 欧美精品啪啪一区二区三区| 最近视频中文字幕2019在线8| 很黄的视频免费| 看黄色毛片网站| 国产一区二区在线观看日韩 | 成人国产综合亚洲| 黄色视频不卡| 伦理电影免费视频| 中文字幕人成人乱码亚洲影| xxxwww97欧美| 久久久久久九九精品二区国产 | 亚洲中文字幕一区二区三区有码在线看 | 国产精品自产拍在线观看55亚洲| 欧美日韩亚洲国产一区二区在线观看| 91字幕亚洲| 1024视频免费在线观看| 99国产精品一区二区三区| 国产欧美日韩精品亚洲av| 欧美极品一区二区三区四区| 国产精品影院久久| 这个男人来自地球电影免费观看| 国产免费男女视频| videosex国产| 亚洲在线自拍视频| www日本黄色视频网| 两性夫妻黄色片| 成人高潮视频无遮挡免费网站| 国产黄a三级三级三级人| 欧洲精品卡2卡3卡4卡5卡区| 国产在线观看jvid| 欧美色欧美亚洲另类二区| 亚洲电影在线观看av| а√天堂www在线а√下载| 国产探花在线观看一区二区| 他把我摸到了高潮在线观看| 特大巨黑吊av在线直播| 波多野结衣高清无吗| 十八禁人妻一区二区| 日本熟妇午夜| 欧美性猛交╳xxx乱大交人| 91大片在线观看| 美女大奶头视频| 可以在线观看的亚洲视频| 精品福利观看| 99国产精品一区二区蜜桃av| 香蕉久久夜色| 亚洲无线在线观看| 亚洲精品av麻豆狂野| 国产免费av片在线观看野外av| 桃色一区二区三区在线观看| 搞女人的毛片| 巨乳人妻的诱惑在线观看| 变态另类丝袜制服| 国产激情偷乱视频一区二区| 成人国产一区最新在线观看| 国产欧美日韩一区二区三| 色播亚洲综合网| 高潮久久久久久久久久久不卡| 国产高清视频在线播放一区| 五月玫瑰六月丁香| 国产成人影院久久av| 久久人妻av系列| 欧美精品亚洲一区二区| 国产免费av片在线观看野外av| 亚洲欧美一区二区三区黑人| 最新美女视频免费是黄的| 一进一出抽搐gif免费好疼| 精品国产乱码久久久久久男人| 在线播放国产精品三级| 色哟哟哟哟哟哟| 露出奶头的视频| 国产久久久一区二区三区| 超碰成人久久| 亚洲真实伦在线观看| 国产亚洲精品久久久久5区| 国产v大片淫在线免费观看| 国产亚洲精品一区二区www| 国产精品综合久久久久久久免费| 亚洲成人精品中文字幕电影| 最近最新免费中文字幕在线| 欧美久久黑人一区二区| 亚洲熟女毛片儿| 国产av不卡久久| 色综合站精品国产| 精品日产1卡2卡| 成人av一区二区三区在线看| 长腿黑丝高跟| 亚洲人成伊人成综合网2020| 超碰成人久久| 国产精品免费一区二区三区在线| 国产精品久久视频播放| 最近最新中文字幕大全电影3| 国内精品一区二区在线观看| 19禁男女啪啪无遮挡网站| 国内精品久久久久久久电影| 少妇熟女aⅴ在线视频| 丰满的人妻完整版| 18禁美女被吸乳视频| 可以在线观看毛片的网站| 草草在线视频免费看| 亚洲五月天丁香| 国内精品久久久久精免费| 精品少妇一区二区三区视频日本电影| 露出奶头的视频| www.精华液| 日本黄色视频三级网站网址| 岛国视频午夜一区免费看| 久99久视频精品免费| av福利片在线观看| 日韩欧美三级三区| 国产麻豆成人av免费视频| 91九色精品人成在线观看| 黄片小视频在线播放| 久久久久国产一级毛片高清牌| 麻豆成人av在线观看| 天堂√8在线中文| bbb黄色大片| 99精品在免费线老司机午夜| 国产一区二区在线观看日韩 | 可以在线观看毛片的网站| 12—13女人毛片做爰片一| 久久久水蜜桃国产精品网| 热99re8久久精品国产| 欧美乱色亚洲激情| 亚洲熟妇熟女久久| 亚洲免费av在线视频| 久久国产精品影院| 久久这里只有精品中国| 久99久视频精品免费| 欧美精品啪啪一区二区三区| 欧美黄色片欧美黄色片| 亚洲一区高清亚洲精品| 一边摸一边做爽爽视频免费| 97人妻精品一区二区三区麻豆| 国产av又大| 成人高潮视频无遮挡免费网站| 婷婷六月久久综合丁香| 麻豆国产av国片精品| 熟妇人妻久久中文字幕3abv| www日本黄色视频网| 欧美成狂野欧美在线观看| 成人一区二区视频在线观看| 精品人妻1区二区| 一个人免费在线观看的高清视频| 国产视频内射| 黄色成人免费大全| 99久久精品热视频| 亚洲国产欧美一区二区综合| 日日摸夜夜添夜夜添小说| 无遮挡黄片免费观看| 国产亚洲精品久久久久5区| 高潮久久久久久久久久久不卡| 亚洲全国av大片| 欧美成人性av电影在线观看| 级片在线观看| 国产高清视频在线播放一区| 亚洲av熟女| 伦理电影免费视频| 嫩草影视91久久| 欧美乱妇无乱码| 好看av亚洲va欧美ⅴa在| 99精品欧美一区二区三区四区| 首页视频小说图片口味搜索| 国产爱豆传媒在线观看 | 亚洲一区二区三区不卡视频| 免费av毛片视频| 日本撒尿小便嘘嘘汇集6| 一二三四在线观看免费中文在| 国产一区二区三区在线臀色熟女| 国产高清videossex| 成人av一区二区三区在线看| 性色av乱码一区二区三区2| 男男h啪啪无遮挡| 亚洲成人精品中文字幕电影| 国产精华一区二区三区| 天天一区二区日本电影三级| 欧美性猛交╳xxx乱大交人| 一级毛片高清免费大全| 九色成人免费人妻av| 亚洲av成人精品一区久久| 18禁国产床啪视频网站| 亚洲avbb在线观看| 亚洲欧美日韩无卡精品| 中亚洲国语对白在线视频| netflix在线观看网站| 长腿黑丝高跟| 人妻久久中文字幕网| 精品电影一区二区在线| 国产精品久久视频播放| 白带黄色成豆腐渣| 亚洲九九香蕉| 亚洲中文日韩欧美视频| 亚洲精品色激情综合| 性欧美人与动物交配| 亚洲中文字幕一区二区三区有码在线看 | 国产三级在线视频| 国产精品久久久久久人妻精品电影| 欧美日韩黄片免| 最近视频中文字幕2019在线8| 精品第一国产精品| 一级a爱片免费观看的视频| 男插女下体视频免费在线播放| 欧美 亚洲 国产 日韩一| 亚洲激情在线av| 亚洲人成伊人成综合网2020| 久久国产精品影院| 香蕉丝袜av| 国产激情偷乱视频一区二区| 亚洲片人在线观看| 很黄的视频免费| 999精品在线视频| 午夜免费激情av| 亚洲专区字幕在线| 国产三级黄色录像| 亚洲欧洲精品一区二区精品久久久| 亚洲精品在线观看二区| 久久久久九九精品影院| 国产精品一区二区三区四区免费观看 | 狠狠狠狠99中文字幕| 日日爽夜夜爽网站| 国产精品,欧美在线| 亚洲欧洲精品一区二区精品久久久| 久久亚洲精品不卡| 久久久久国产一级毛片高清牌| 999久久久国产精品视频| 麻豆国产av国片精品| 日本黄大片高清| 毛片女人毛片| 一二三四在线观看免费中文在| 国内毛片毛片毛片毛片毛片| 日日夜夜操网爽| 天堂动漫精品| 国产激情久久老熟女| 午夜影院日韩av| 97超级碰碰碰精品色视频在线观看| 神马国产精品三级电影在线观看 | 不卡一级毛片| 亚洲精华国产精华精| 国产亚洲精品一区二区www| 国产精品日韩av在线免费观看| 日本一本二区三区精品| 中文字幕人成人乱码亚洲影| 非洲黑人性xxxx精品又粗又长| 91字幕亚洲| 操出白浆在线播放| 三级国产精品欧美在线观看 | av视频在线观看入口| 99国产精品99久久久久| 黄片小视频在线播放| 在线视频色国产色| 久久天躁狠狠躁夜夜2o2o| 欧美乱码精品一区二区三区| 亚洲精品美女久久av网站| 最近最新中文字幕大全电影3| 午夜福利欧美成人| 精品欧美一区二区三区在线| 人人妻,人人澡人人爽秒播| 国产真实乱freesex| 身体一侧抽搐| 久久久国产成人免费| 免费看a级黄色片| 亚洲精品国产一区二区精华液| 美女黄网站色视频| 99久久99久久久精品蜜桃| 69av精品久久久久久| 亚洲成人免费电影在线观看| 国产成人一区二区三区免费视频网站| 一a级毛片在线观看| 亚洲人成网站高清观看| av在线天堂中文字幕| 欧美不卡视频在线免费观看 | www.自偷自拍.com| 精品久久久久久成人av| 国产高清视频在线观看网站| 国产亚洲精品综合一区在线观看 | 999精品在线视频| 欧美色欧美亚洲另类二区| 欧美黑人精品巨大| 日日爽夜夜爽网站| 大型av网站在线播放| 亚洲熟女毛片儿| 久久这里只有精品19| 巨乳人妻的诱惑在线观看| 久久国产精品人妻蜜桃| 欧美性猛交╳xxx乱大交人| 国产精品1区2区在线观看.| 国产熟女午夜一区二区三区| 午夜影院日韩av| 国产高清videossex| 国产三级黄色录像| 老熟妇乱子伦视频在线观看| 久久久国产成人免费| 亚洲国产精品sss在线观看| 亚洲天堂国产精品一区在线| 露出奶头的视频| 国语自产精品视频在线第100页| 久久九九热精品免费| 国产三级在线视频| 最新美女视频免费是黄的| or卡值多少钱| 一二三四在线观看免费中文在| 欧美日韩福利视频一区二区| 国产在线观看jvid| 高潮久久久久久久久久久不卡| 国内毛片毛片毛片毛片毛片| 午夜两性在线视频| 亚洲免费av在线视频| 1024香蕉在线观看| 国产熟女xx| 久久精品成人免费网站| 人人妻,人人澡人人爽秒播| 色尼玛亚洲综合影院| 欧美一区二区国产精品久久精品 | 香蕉丝袜av| 日韩中文字幕欧美一区二区| 成年免费大片在线观看| 免费在线观看完整版高清| 国产午夜精品论理片| 在线观看午夜福利视频| 亚洲精品在线观看二区| 中文字幕最新亚洲高清| 听说在线观看完整版免费高清| 小说图片视频综合网站| 97超级碰碰碰精品色视频在线观看| 他把我摸到了高潮在线观看| 黑人操中国人逼视频| 丝袜人妻中文字幕| 国产亚洲精品第一综合不卡| 最新美女视频免费是黄的| 久久中文字幕人妻熟女| 夜夜看夜夜爽夜夜摸| 欧美色欧美亚洲另类二区| 久久精品夜夜夜夜夜久久蜜豆 | 色哟哟哟哟哟哟| 久久国产乱子伦精品免费另类| 欧美zozozo另类| 一级毛片高清免费大全| a级毛片a级免费在线| 精品久久久久久久人妻蜜臀av| av有码第一页| 人人妻人人看人人澡| 俄罗斯特黄特色一大片| 亚洲va日本ⅴa欧美va伊人久久| 69av精品久久久久久| 久久国产精品影院| 国产精华一区二区三区| 亚洲美女黄片视频| 淫妇啪啪啪对白视频| 一夜夜www| 少妇粗大呻吟视频| 日本三级黄在线观看| 亚洲狠狠婷婷综合久久图片| 夜夜看夜夜爽夜夜摸| 狂野欧美激情性xxxx| 亚洲精品美女久久av网站| 亚洲av五月六月丁香网| 99热6这里只有精品| 国产精品免费一区二区三区在线| 亚洲自偷自拍图片 自拍| 在线观看免费日韩欧美大片| 久久香蕉激情| 亚洲国产看品久久| 看片在线看免费视频| 亚洲国产欧美一区二区综合| 好男人电影高清在线观看| 亚洲第一电影网av| 香蕉丝袜av| 悠悠久久av| svipshipincom国产片| 听说在线观看完整版免费高清| 精品国产亚洲在线| 精品午夜福利视频在线观看一区| 国产亚洲欧美在线一区二区| 在线观看免费视频日本深夜| 久久精品国产99精品国产亚洲性色| 久久久久久久久久黄片| 国产精品国产高清国产av| 国产成人一区二区三区免费视频网站| 免费电影在线观看免费观看| 国产亚洲精品一区二区www| 最近在线观看免费完整版| 午夜a级毛片| 亚洲成av人片在线播放无| 亚洲成av人片免费观看| 日韩精品免费视频一区二区三区| 国产亚洲精品综合一区在线观看 | 亚洲欧美精品综合一区二区三区| 两人在一起打扑克的视频| 波多野结衣高清作品| 婷婷精品国产亚洲av| 国产精品亚洲av一区麻豆| 国产黄a三级三级三级人| 日本成人三级电影网站| 久久精品国产99精品国产亚洲性色| 国产一区二区在线av高清观看| 亚洲精品一卡2卡三卡4卡5卡| 亚洲免费av在线视频| 黄色视频不卡| 国产亚洲av高清不卡| 欧美一级毛片孕妇| 亚洲无线在线观看| 999久久久精品免费观看国产| 亚洲男人的天堂狠狠| 国产精品av久久久久免费| 成人av一区二区三区在线看| 国产成人啪精品午夜网站| 免费看美女性在线毛片视频| ponron亚洲|