• <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 ?

    游離氨對活性污泥系統(tǒng)中脫氮性能及胞外聚合物的影響

    2021-03-11 08:49蔡晨健吳常峰楊浩陳桐生孫洪偉
    土木建筑與環(huán)境工程 2021年1期
    關(guān)鍵詞:多糖蛋白質(zhì)

    蔡晨健 吳常峰 楊浩 陳桐生 孫洪偉

    摘 要:以人工模擬廢水為研究對象,采用4組SBR反應(yīng)器(R0.5、R5、R10和R15),考察了4種游離氨濃度(0.5、5、10和15 mg/L)對生物脫氮效能、胞外聚合物含量及其組分(蛋白質(zhì)(PN)、多糖(PS)和核酸(DNA))影響。結(jié)果表明,4種游離氨濃度條件下都實(shí)現(xiàn)了較高的脫氮效果(97.6%~99.4%)。游離氨對3種胞外聚合物(LB-EPS、TB-EPS、總EPS)及其組分有顯著影響。當(dāng)游離氨濃度從0.5 mg/L 增加到10 mg/L時(shí),LB-EPS、TB-EPS、總EPS的含量及其組分的含量都顯著增加;當(dāng)游離氨濃度進(jìn)一步增加到15 mg/L時(shí),LB-EPS、TB-EPS、總EPS的含量及其組分的含量都呈降低的趨勢;在4個(gè)游離氨濃度下,PN是LB-EPS的主要成分,PS是TB-EPS和總EPS的主要成分;在4個(gè)游離氨濃度下的整個(gè)反應(yīng)周期中,3種胞外聚合物及其組分的含量都跟NO-x—N有著相同的變化趨勢。

    關(guān)鍵詞:游離氨;脫氮;胞外聚合物;蛋白質(zhì);多糖

    1 Introduction

    Extracellular polymeric substances(EPS) accumulating on the surface of activated sludge account for 80% of the activated sludge matrix, and play a significant role on wastewater treatment[1-2].

    Ammonia nitrogenis the main pollutant in multiple wastewaters. Therefore, there must be a certain concentration of free ammonia(FA) in the presence of NH+4—N in any wastewater. The concentration of free ammonia mainly depends on the values of NH+4—N, temperature and pH of the wastewater[3]. In recent decades, increasing efforts have been devoted to investigating the effects and mechanisms of free ammonia on nitrification, denitrification, Anammox, phosphorus removal and anaerobic digestion processes [4-7]. But limited literature has reported the effects of free ammonia on extracellular polymeric substance and its components (including proteins, polysaccharides and DNA). Zhang et al.[8] reported that free ammonia pretreatment, with the concentration controlled at 176.5 mg/L, can facilitate the breakdown of extracellular polymeric substances and kill the living cells. But the effects of low concentrations of free ammonia on the production of extracellular polymeric substances and their components are still unknown.

    In addition, with respect to the main components of extracellular polymeric substances, there are some different findings. Some studies have reported that polysaccharides(PS) were the predominant components of extracellular polymeric substances [9-10], while other studies have found that proteins(PN) were the main components[11-12]. Furthermore, it was reported that extracellular polymeric substances have some different vital functions as the main components in activated sludge differed. Higher tightly bound extracellular polymeric substance(TB-EPS) contents have been reported to noticeably enable the extracellular polymeric substance to form flocs in activated sludge [13]. Moreover, protein enrichment in the tightly bound extracellular polymeric substance has positive effects on the sedimentation and dehydration of the activated sludge[9,14]. However, it was reported that excessive extracellular polymeric substance contents, especially polysaccharide enriched loosely bound extracellular polymeric substance(LB-EPS), can induce poor dewaterability and bioflocculation[9,14]. The effects of the concentration of free ammonia on the predominant components of extracellular polymeric substance are still unknown. Hence, it is necessary to research the main components of extracellular polymeric substances under different concentratiosns of free ammonia.

    Therefore, the objectives of this study were to elucidate the effects of free ammonia on the production of three kinds of extracellular polymeric substance (loosely bound extracellular polymeric substance, tightly bound extracellular polymeric substance and total extracellular polymeric substance) and their components and to build a correlation between nitrogen variation and the production of the three kinds of extracellular polymeric substances and their components under four different concentrations of free ammonia.

    2 Material and methods

    2.1 Experimental set-up and operational procedure

    Four bench-scale sequencing batch reactors(SBR) made of plexiglass15 cm in diameter with 5 L working volume and 40 cm height were used in the present study. The sequencing batch reactors were operated at four different concentrations of free ammonia (0.5, 5, 10 and 15 mg/L, respectively). The long-term operations (lasted for 244 days) were carried out in four sequencing batch reactors fed with synthetic wastewater. The operational cycles of the four sequencing batch reactors with varying concentrations of free ammonia (R0.5, R5, R10 and R15) consisted of influent, aerobic reaction, anoxic reaction, settling, decanting and idle. Table 1 shows details of the operational conditions of the four sequencing batch reactors during the entire experimental cycle.

    2.2 Inoculated sludge and influent contents

    Inoculated activated sludge was collected froma plant mainly treating domestic and brewery wastewater (accounted for about 60%~70% and 30%~40%, respectively). The plant was located at Lanzhou, Gansu province in China, where the anaerobic-anoxic-oxic process was employed. The initial concentration of the mixed liquor suspended solids was 3 000 mg/L. The inoculated sludge was domesticated for 20 days and fed with synthetic wastewater with the following composition per liter: 115 mg of NH4Cl, 385 mg of CH3COONa, 26 mg of KH2PO4 and trace element solution. The trace element solution consisted of MgSO4·7H2O 5.07 mg/L, MnSO4·4H2O 0.31 mg/L, FeSO4·7H2O 2.49 mg/L, CuSO4 0.25 mg/L, Na2MoO4·2H2O 1.26 mg/L, ZnSO4·7H2O 0.44 mg/L, NaCl 0.25 mg/L, CaSO4·2H2O 0.43 mg/L, CoCl2·6H2O 0.41 mg/L, EDTA 1.88 mg/L. Table 1 presents a summary of the characteristics of the influent of the four sequence batch reactors.

    2.3 Extracellular polymeric substance extraction

    With respect to extracellular polymeric substance extraction, it mainly included loosely bound extracellular polymeric substance and tightly bound extracellular polymeric substance extraction. The modified two-step thermal extraction method was used to extract loosely bound extracellular polymeric substance and tightly bound extracellular polymeric substance[15]. In the present study, the total extracellular polymeric substance content was regarded as the sum of the loosely bound extracellular polymeric substance and the tightly bound extracellular polymeric substance fractions.

    Fig.1(b) and (c) show the concentration and variation of NO-2-N and NO-3-N during the whole reaction cycle under different concentrations of free ammonia. The oxidization of NH+4—N to NO-2-N was mainly achieved at R10 and R15 with the nitrite accumulation rate stable in 96.6%~99.3% (since 80 cycles), which shows that partial nitrification was achieved at R10 and R15 (NH+4—N→NO-2-N→N2).NH+4—N convert to NO-3-N was achieved at R0.5 and R5 with the nitrite accumulation lower than 6.3% during the whole reaction, suggesting that R0.5 and R5 were during the full nitrification process (NH+4—N→NO-2-N→NO-3-N→NO-2-N→N2). This shows that high free ammonia concentration was beneficial to the formation of partial nitrification. Liu et al.[21] found that higher free ammonia concentration was conducive to the realization of partial nitrification as the free ammonia exerted a stronger inhibition on nitrite oxidation than on ammonium oxidation.

    The correlation between free ammonia concentration and nitrogen consumption during the nitrification process was studied (data not shown). Nitrogen consumption increased from 7.0 mg/L at 0.5 mg/L free ammonia to 31.5 mg/L at 10 mg/L free ammonia, and then subsequently decreased to 14.2 mg/L at 15 mg/L free ammonia, which indicated that high nitrogen removal efficiency was available through added free ammonia concentration. Wang et al.[22]? found that the nitrogen removal was significantly improved after free ammonia pretreatment in sequencing batch reactors treating synthetic wastewater.

    3.2 Production of three kinds of extracellular polymeric substance and their components under different concentrations of free ammonia

    Fig.2 shows the comparison of the total contents of extracellular polymeric substance, tightly bound extracellular polymeric substance and loosely bound extracellular polymeric substance under different concentrations of free ammonia. Although the contents of total extracellular polymeric substance, tightly bound extracellular polymeric substance and loosely bound extracellular polymeric substance all showed upward trend with the free ammonia concentrations increased from 0.5 to 10 mg/L, they all showed downward trend when free ammonia concentrations continue increased to 15 mg/L, indicating that the free ammonia concentration was certainly correlated with extracellular polymeric substance production. The mechanism of this phenomenon was that microorganism would produce amount of extracellular polymeric substance to ensure microorganism can survival in toxic environmental condition. However, the contents of total extracellular polymeric substance, tightly bound extracellular polymeric substance and loosely bound extracellular polymeric substance all decreased at 15 mg/L free ammonia by comparison with the 10 mg/L of free ammonia, which showed that the auto-protection ability of the microorganism was limited, so that the higher free ammonia concentrations can cause cell inactivation due to the biocidal impact of free ammonia, which triggers the reduction of metabolites, resulting in extracellular polymeric substance reduction.

    Fig.3 (a), (b) and (c) show the effects of different concentrations of free ammonia on proteins, polysaccharides and DNA in total extracellular polymeric substance, tightly bound extracellular polymeric substance and loosely bound extracellular polymeric substance. The protein and polysaccharide contents in the three fractions of extracellular polymeric substance all showed an upward trend as the free ammonia concentrations was increased from 0.5 to 10 mg/L. However, when the free ammonia concentrations further increased to 15 mg/L, the protein and polysaccharide contents in the three fractions extracellular polymeric substance all showed a downward trend. The DNA content gradually increased as the free ammonia increased, which shows the concentration of free ammonia can cause cell inactivation. Generally, the contents of the three kinds of extracellular polymeric substances and their components increased as the free ammonia concentration increased, triggered by the denser layers of loosely bound extracellular polymeric substance and tightly bound extracellular polymeric substance, which can stop free ammonia from diffusing into the interior of the activated sludge and reduce the free ammonia toxicity to bacteria [23].

    Fig.3(d) shows the percentage of the protein polysaccharide and DNA contents in the three assessed extracellular polymeric substance fractions under four different free ammonia conditions. It can be seen that polysaccharides accounted for between 47.1% and 55.8% of the tightly bound extracellular polymeric substance and total extracellular polymeric substance under four concentrations of free ammonia, followed by proteins (39.8%~46.2%) and DNA (4.2%~7.1%), indicating that polysaccharides were the main component at these four free ammonia conditions. Especially, the protein contents and DNA of the tightly bound extracellular polymeric substance and total extracellular polymeric substance was augmented, while the polysaccharide content decreased as the concentration of free ammonia increased from 0.5 to 15 mg/L.

    However, a discrepancy was observed in loosely bound extracellular polymeric substance. Proteins were the dominant component of the loosely bound extracellular polymeric substance (44.3%~64.2%), while polysaccharides was the second largest component (32.8%~53.3%) and DNA was the smallest component (2.4%~3.1%). Furthermore, we found that the percentage of polysaccharides of the loosely bound extracellular polymeric substance was augmented with the increase in the concentration of free ammonia from 0.5 to 10 mg/L, while the percentage of polysaccharides decreased when the concentration of free ammonia was increased to 15 mg/L. An opposite trend was observed in the percentage of proteins of the loosely bound extracellular polymeric substances.

    3.3 Variation of extracellular polymeric substance and nitrogen in a typical sequencing batch reactor cycle under different concentrations of free ammoniaTo better evaluate the reactor performance, a typical sequencing batch reactors cycle (201 cycle) was examined during nitrification and dentrification under four different concentrations of free ammonia (Fig.4). Three kinds of extracellular polymeric substance and their components showed an upward trend during the nitrification process, then a downward trend during the denitrification process under the four different concentrations of free ammonia, except for the DNA content. The trend of the total extracellular polymeric substance and its components was negatively correlated with the NH+4—N value (R=-0.787 to -0.856, p<0.05) in the four kinds of free ammonia conditions during the nitrification process, but was positively correlated with the NO-3-N value (R=0.645 to 0.699, p<0.05) in R0.5 and R5 and the NO-2—N value (R=0.654 to 0.701, p<0.05) in R10 and R15 during the whole reaction cycle, suggesting that certain correlations were stored intracellularly. Sheng et al.[1] believed that the negatively charged proteins are always binding with the positively charged NH+4—N through electrostatic interaction. Hence, more proteins were produced to provide sites for the adsorption of NH+4—N. Then the NH-4—N was further degraded by nitrifying bacteria, resulting in the increase in NO-x—N and the protein content during the nitrification process, while the polysaccharide content was reduced during the subsequent denitrification process. The main reason for this was that the extracellular polymeric substance served as an energy source and was utilized by denitrifying bacteria to perform denitrification, which led to the reduction of NO-x—N and the total extracellular polymeric substance and its components[24-25].

    4 Conclusions

    This paper has presented a comparative study of three kinds of extracellular polymeric substances and their components, as well as the nitrogen removal performance of the influent at different concentrations of free ammonia. The following conclusions may be drawn from this study:

    1)Free ammonia concentration at less than 15 mg/L had no obvious effect on the nitrogen removal performance of the sequencing batch reactors.

    2)Free ammonia promoted the production of loosely bound extracellular polymeric substance, tightly bound extracellular polymeric substance and their components when its concentration increased from 0.5 to 10 mg/L. However, an opposite result was observed when its concentration was increased to 15 mg/L.

    3)Polysaccharides dominated in the tightly bound extracellular polymeric substance and total extracellular polymeric substance fractions, while proteins dominated in the loosely bound extracellular polymeric substance fraction under four different concentrations of free ammonia.

    4) The variation of three kinds of extracellular polymeric substance and their components was completely opposite the variation of NH+4—N during nitrification, but it was consistent with the variation of NO-x—N during the whole reaction cycle under the four different concentrations of free ammonia.

    Acknowledgements

    The authors would like to acknowledge the financial support from the National Natural Science Foundation of China (Grant No. 51668031).

    References:

    [1] SHENG G P, YU H Q, LI X Y. Extracellular polymeric substances (EPS) of microbial aggregates in biological wastewater treatment systems:A review [J]. Biotechnology Advances, 2010, 28(6): 882-894.

    [2] SHI Y H, HUANG J H, ZENG G M, et al. Exploiting extracellular polymeric substances (EPS) controlling strategies for performance enhancement of biological wastewater treatments:An overview [J]. Chemosphere, 2017, 180: 396-411.

    [3] ANTHONISEN A C, LOEHR R C, PRAKASAM T B, et al. Inhibition of nitrification by ammonia and nitrous acid [J]. Journal-Water Pollution Control Federation, 1976, 48(5): 835-852.

    [4] CHUNG J, SHIM H, LEE Y W, et al. Comparison of influence of free ammonia and Dissolved oxygen on nitrite accumulation between suspended and attached cells [J]. Environmental Technology, 2005, 26(1): 21-33.

    [5] YANG G J, XU Q X, WANG D B, et al. Free ammonia-based sludge treatment reduces sludge production in the wastewater treatment process [J]. Chemosphere, 2018, 205: 484-492.

    [6] AKTAN C K, YAPSAKLI K, MERTOGLU B. Inhibitory effects of free ammonia on Anammox bacteria [J]. Biodegradation, 2012, 23(5): 751-762.

    [7] CALLI B, MERTOGLU B, INANC B, et al. Effects of high free ammonia concentrations on the performances of anaerobic bioreactors [J]. Process Biochemistry, 2005, 40(3/4): 1285-1292.

    [8] ZHANG C, QIN Y G, XU Q X, et al. Free ammonia-based pretreatment promotes short-chain fatty acid production from waste activated sludge [J]. ACS Sustainable Chemistry & Engineering, 2018, 6(7): 9120-9129.

    [9] BASUVARAJ M, FEIN J, LISS S N. Protein and polysaccharide content of tightly and loosely bound extracellular polymeric substances and the development of a granular activated sludge floc [J]. Water Research, 2015, 82: 104-117.

    [10] SHAO Y X, ZHANG H X, BUCHANAN I, et al. Comparison of extracellular polymeric substance (EPS) in nitrification and nitritation bioreactors [J]. International Biodeterioration & Biodegradation, 2019, 143: 104713.

    [11] HAN X M, ZHOU Z, MEI X J, et al. Influence of fermentation liquid from waste activated sludge on anoxic/oxic- membrane bioreactor performance: Nitrogen removal, membrane fouling and microbial community [J]. Bioresource Technology, 2018, 250: 699-707.

    [12] DASGUPTA S, DE CLIPPELEIR H, GOEL R. Short operational differences support granulation in a lab scale reactor in comparison to another conventional activated sludge reactor [J]. Bioresource Technology, 2019, 271: 417-426.

    [13] ZENG T T, RENE E R, ZHANG S Q, et al. Removal of selenate and cadmium by anaerobic granular sludge: EPS characterization and microbial community analysis [J]. Process Safety and Environmental Protection, 2019, 126: 150-159.

    [14] LI X Y, YANG S F. Influence of loosely bound extracellular polymeric substances (EPS) on the flocculation, sedimentation and dewaterability of activated sludge [J]. Water Research, 2007, 41(5): 1022-1030.

    [15] CAO Z P, ZHANG H W, ZHANG J L. Effects of sludge retention time on the sludge characteristics and membrane fouling in membrane bioreactor [J]. China Environmental Science, 2009, 29(4): 386-390.

    [16] FRLUND B, PALMGREN R, KEIDING K, et al. Extraction of extracellular polymers from activated sludge using a cation exchange resin [J]. Water Research, 1996, 30(8): 1749-1758.

    [17] MASUKO T, MINAMI A, IWASAKI N, et al. Carbohydrate analysis by a phenol-sulfuric acid method in microplate format [J]. Analytical Biochemistry, 2005, 339(1): 69-72.

    [18] MENGISTU Y, EDWARDS C, SAUNDERS J R. Continuous culture studies on the synthesis of capsular polysaccharide by Klebsiella pneumoniae K1 [J]. The Journal of Applied Bacteriology, 1994, 76(5): 424-430.

    [19] APHA. Standard methods for the examination of water and wastewater [S]. Twentieth ed. American Public Health Association, Washington, DC, USA, 1998.

    [20] XU Q X, LIU X R, WANG D B, et al. Free ammonia-based pretreatment enhances phosphorus release and recovery from waste activated sludge [J]. Chemosphere, 2018, 213: 276-284.

    [21] LIU Y W, NGO HH, GUO W S, et al. The roles of free ammonia (FA) in biological wastewater treatment processes: A review [J]. Environment International, 2019, 123: 10-19.

    [22] WANG Q L, DUAN H R, WEI W, et al. Achieving stable mainstream nitrogen removal via the nitrite pathway by sludge treatment using free ammonia [J]. Environmental Science & Technology, 2017, 51(17): 9800-9807.

    [23] MA B R, LI Z W, WANG S, et al. Insights into the effect of nickel (Ni(II)) on the performance, microbial enzymatic activity and extracellular polymeric substances of activated sludge [J]. Environmental Pollution, 2019, 251: 81-89.

    [24] MORGAN J W, FORSTER C F, EVISON L. A comparative study of the nature of biopolymers extracted from anaerobic and activated sludges [J]. Water Research, 1990, 24(6): 743-750.

    [25] HOA P T, NAIR L, VISVANATHAN C. The effect of nutrients on extracellular polymeric substance production and its influence on sludge properties [J]. Water SA, 2004, 29(4): 437-442.

    (編輯 胡英奎)

    猜你喜歡
    多糖蛋白質(zhì)
    藍(lán)莓多糖提取與工藝優(yōu)化的研究
    香菇多糖水解產(chǎn)物中葡萄糖的分離及其測定
    優(yōu)質(zhì)蛋白質(zhì)與免疫力
    云南產(chǎn)地參多糖脫色、脫蛋白及其抗凝血活性研究
    蛋白質(zhì)也分三六九等
    滸苔多糖的提取工藝研究
    金頂側(cè)耳菌菇多糖提取工藝的比較
    正交試驗(yàn)對甘蔗渣多糖超聲波提取工藝的優(yōu)化
    魚中蛋白質(zhì)測定方法的探討
    DNA與蛋白質(zhì)的相互作用
    王馨瑶露胸无遮挡在线观看| 18在线观看网站| 91麻豆av在线| 一级毛片精品| 天堂俺去俺来也www色官网| 欧美97在线视频| 免费高清在线观看日韩| 三级毛片av免费| 一级毛片女人18水好多| 在线观看www视频免费| 在线观看免费视频网站a站| 大陆偷拍与自拍| 中文欧美无线码| 欧美另类一区| 久久久精品区二区三区| 一二三四社区在线视频社区8| 中国美女看黄片| 国产激情久久老熟女| 99久久99久久久精品蜜桃| 飞空精品影院首页| 在线天堂中文资源库| 国产精品偷伦视频观看了| 777米奇影视久久| 精品卡一卡二卡四卡免费| 欧美亚洲日本最大视频资源| 精品一品国产午夜福利视频| 国产精品 国内视频| 欧美一级毛片孕妇| 亚洲专区国产一区二区| 宅男免费午夜| 麻豆国产av国片精品| 国产一区二区 视频在线| 一边摸一边抽搐一进一出视频| av在线老鸭窝| 国产有黄有色有爽视频| 色综合欧美亚洲国产小说| 天天躁日日躁夜夜躁夜夜| 亚洲av成人不卡在线观看播放网 | av又黄又爽大尺度在线免费看| 丝袜美足系列| 亚洲伊人色综图| 90打野战视频偷拍视频| 女人精品久久久久毛片| av不卡在线播放| 91成人精品电影| 免费高清在线观看日韩| 爱豆传媒免费全集在线观看| 午夜福利影视在线免费观看| 国产xxxxx性猛交| 俄罗斯特黄特色一大片| 免费在线观看黄色视频的| 国产成人av激情在线播放| 国产精品国产三级国产专区5o| 国产一卡二卡三卡精品| 最黄视频免费看| xxxhd国产人妻xxx| www.自偷自拍.com| 最近中文字幕2019免费版| 国产精品秋霞免费鲁丝片| 看免费av毛片| 精品人妻一区二区三区麻豆| 俄罗斯特黄特色一大片| 法律面前人人平等表现在哪些方面 | 一区二区日韩欧美中文字幕| 丝袜人妻中文字幕| 久久影院123| 一级黄色大片毛片| 欧美午夜高清在线| 美女主播在线视频| 91精品国产国语对白视频| 纯流量卡能插随身wifi吗| 欧美日本中文国产一区发布| 色婷婷av一区二区三区视频| 色老头精品视频在线观看| 巨乳人妻的诱惑在线观看| 亚洲一码二码三码区别大吗| 亚洲精品国产色婷婷电影| 97精品久久久久久久久久精品| 人妻 亚洲 视频| 亚洲精华国产精华精| 男女国产视频网站| 少妇粗大呻吟视频| 日韩欧美免费精品| 国产精品 欧美亚洲| 97精品久久久久久久久久精品| 亚洲精品一二三| 久久九九热精品免费| 淫妇啪啪啪对白视频 | 男女免费视频国产| 久久ye,这里只有精品| 精品少妇一区二区三区视频日本电影| 少妇被粗大的猛进出69影院| 欧美成狂野欧美在线观看| 淫妇啪啪啪对白视频 | 嫁个100分男人电影在线观看| 搡老乐熟女国产| 999久久久精品免费观看国产| 亚洲精品美女久久久久99蜜臀| 午夜精品久久久久久毛片777| 中文字幕av电影在线播放| 成年av动漫网址| 最近中文字幕2019免费版| 精品久久蜜臀av无| 日韩一区二区三区影片| 90打野战视频偷拍视频| 多毛熟女@视频| 黑人巨大精品欧美一区二区mp4| 1024香蕉在线观看| 精品国产一区二区久久| 五月天丁香电影| 久久亚洲精品不卡| 亚洲五月婷婷丁香| 久久青草综合色| 黑人巨大精品欧美一区二区蜜桃| 亚洲黑人精品在线| 久久久久久久精品精品| av在线老鸭窝| 国产一区二区三区av在线| 脱女人内裤的视频| 巨乳人妻的诱惑在线观看| 大型av网站在线播放| 婷婷丁香在线五月| 日韩中文字幕欧美一区二区| 精品久久久久久久毛片微露脸 | 伊人久久大香线蕉亚洲五| 免费高清在线观看日韩| 伦理电影免费视频| 在线观看www视频免费| 啦啦啦 在线观看视频| 亚洲国产av新网站| 水蜜桃什么品种好| 19禁男女啪啪无遮挡网站| 操美女的视频在线观看| 99热全是精品| 最近中文字幕2019免费版| 大码成人一级视频| 少妇粗大呻吟视频| 交换朋友夫妻互换小说| 欧美久久黑人一区二区| 久久精品国产a三级三级三级| 中文字幕人妻丝袜制服| 久久午夜综合久久蜜桃| 午夜免费成人在线视频| 亚洲精华国产精华精| 精品一区二区三区av网在线观看 | 国产欧美日韩一区二区三区在线| 亚洲精品中文字幕一二三四区 | 秋霞在线观看毛片| 国产精品一区二区在线观看99| 99久久精品国产亚洲精品| 欧美国产精品va在线观看不卡| 人妻 亚洲 视频| 国产一区二区三区av在线| 精品少妇内射三级| 亚洲精品久久成人aⅴ小说| 久久久久国内视频| 丰满少妇做爰视频| 国产精品国产av在线观看| 香蕉国产在线看| 美女福利国产在线| 午夜福利乱码中文字幕| 日韩有码中文字幕| 亚洲一区中文字幕在线| 精品人妻熟女毛片av久久网站| 国产成人一区二区三区免费视频网站| 日韩 亚洲 欧美在线| 精品乱码久久久久久99久播| 最新在线观看一区二区三区| 建设人人有责人人尽责人人享有的| 国产欧美亚洲国产| 欧美一级毛片孕妇| 亚洲国产欧美日韩在线播放| 99国产精品一区二区蜜桃av | 777米奇影视久久| 精品少妇一区二区三区视频日本电影| 黄色视频,在线免费观看| 精品久久蜜臀av无| 此物有八面人人有两片| 久久精品成人免费网站| 精品久久久久久久人妻蜜臀av| 国产成人系列免费观看| 国产亚洲av嫩草精品影院| 国产亚洲精品av在线| 男人舔女人下体高潮全视频| 1024手机看黄色片| 国产精品1区2区在线观看.| 欧美黑人欧美精品刺激| 国产单亲对白刺激| 久久精品91蜜桃| a级毛片a级免费在线| 成人亚洲精品av一区二区| 亚洲电影在线观看av| 一个人免费在线观看的高清视频| 国产精品 欧美亚洲| 99久久久亚洲精品蜜臀av| 一个人免费在线观看的高清视频| 国产又黄又爽又无遮挡在线| 亚洲欧美日韩无卡精品| 麻豆成人午夜福利视频| 熟妇人妻久久中文字幕3abv| 亚洲av成人av| 亚洲国产精品久久男人天堂| 日韩欧美 国产精品| 日本免费a在线| 中文字幕最新亚洲高清| 日本五十路高清| 亚洲aⅴ乱码一区二区在线播放 | 国产高清有码在线观看视频 | 国产在线观看jvid| 香蕉国产在线看| 香蕉久久夜色| 黄色视频不卡| 一本精品99久久精品77| 色噜噜av男人的天堂激情| 午夜精品在线福利| 亚洲国产精品合色在线| 亚洲性夜色夜夜综合| 国产精品久久电影中文字幕| 亚洲真实伦在线观看| 欧美黑人巨大hd| 午夜精品一区二区三区免费看| 日韩欧美精品v在线| www.www免费av| 黄色毛片三级朝国网站| 亚洲片人在线观看| 日本一区二区免费在线视频| 变态另类成人亚洲欧美熟女| 日本免费a在线| 国产精品一区二区免费欧美| 国产一区在线观看成人免费| 热99re8久久精品国产| 国产黄片美女视频| 丝袜美腿诱惑在线| 欧美久久黑人一区二区| 久久99热这里只有精品18| 操出白浆在线播放| 妹子高潮喷水视频| 大型av网站在线播放| 啦啦啦韩国在线观看视频| 国产一区在线观看成人免费| 国内精品久久久久久久电影| 一边摸一边做爽爽视频免费| 精品免费久久久久久久清纯| 成人精品一区二区免费| 美女高潮喷水抽搐中文字幕| 色av中文字幕| 久久久久亚洲av毛片大全| 丝袜人妻中文字幕| 久久久久国产精品人妻aⅴ院| 国产精品日韩av在线免费观看| 蜜桃久久精品国产亚洲av| 又粗又爽又猛毛片免费看| 久久天躁狠狠躁夜夜2o2o| 波多野结衣巨乳人妻| 亚洲激情在线av| 欧美丝袜亚洲另类 | 亚洲精品美女久久久久99蜜臀| 精品日产1卡2卡| 国内少妇人妻偷人精品xxx网站 | 午夜精品一区二区三区免费看| 精华霜和精华液先用哪个| 国产欧美日韩一区二区精品| 婷婷精品国产亚洲av| 久久中文字幕一级| 波多野结衣巨乳人妻| 国产精品免费一区二区三区在线| 亚洲avbb在线观看| 人人妻人人澡欧美一区二区| 男插女下体视频免费在线播放| 超碰成人久久| 成人永久免费在线观看视频| 久久精品综合一区二区三区| 看免费av毛片| 久久久久久久久久黄片| 亚洲男人的天堂狠狠| 欧美又色又爽又黄视频| 可以在线观看的亚洲视频| 黑人巨大精品欧美一区二区mp4| 搡老妇女老女人老熟妇| 欧美乱码精品一区二区三区| 国产一区二区在线av高清观看| √禁漫天堂资源中文www| 国产精品久久久久久亚洲av鲁大| 一进一出抽搐动态| 亚洲精品在线美女| 黄片大片在线免费观看| 欧美日韩精品网址| а√天堂www在线а√下载| 99国产精品99久久久久| 国产高清视频在线观看网站| 亚洲av成人精品一区久久| 一区福利在线观看| 亚洲一区高清亚洲精品| 久久欧美精品欧美久久欧美| 国产麻豆成人av免费视频| 成人特级黄色片久久久久久久| 欧美成人性av电影在线观看| 一本精品99久久精品77| 99久久久亚洲精品蜜臀av| 国产又色又爽无遮挡免费看| 神马国产精品三级电影在线观看 | 在线观看免费午夜福利视频| 中文字幕av在线有码专区| 国产在线观看jvid| 这个男人来自地球电影免费观看| 欧美久久黑人一区二区| 国产精品综合久久久久久久免费| 亚洲无线在线观看| 91麻豆av在线| 欧美日韩精品网址| 在线免费观看的www视频| 麻豆国产av国片精品| 国产激情偷乱视频一区二区| 999久久久国产精品视频| 成在线人永久免费视频| 美女扒开内裤让男人捅视频| 精品不卡国产一区二区三区| 麻豆国产97在线/欧美 | 国产伦一二天堂av在线观看| 国产成人系列免费观看| 十八禁人妻一区二区| 脱女人内裤的视频| 国产精品影院久久| 丝袜美腿诱惑在线| 最新美女视频免费是黄的| 999久久久国产精品视频| 欧美成人性av电影在线观看| 免费观看精品视频网站| 男女午夜视频在线观看| 在线观看免费日韩欧美大片| 变态另类成人亚洲欧美熟女| 国产成人影院久久av| 成年版毛片免费区| 欧美zozozo另类| 亚洲欧美日韩东京热| av在线天堂中文字幕| 精品久久久久久久人妻蜜臀av| 亚洲熟妇中文字幕五十中出| 窝窝影院91人妻| 国产成年人精品一区二区| 国产aⅴ精品一区二区三区波| 一a级毛片在线观看| 欧美3d第一页| 国产三级在线视频| 最新在线观看一区二区三区| 国产成人系列免费观看| 欧美丝袜亚洲另类 | 91av网站免费观看| 黑人操中国人逼视频| 欧美性猛交黑人性爽| 免费在线观看日本一区| 国产日本99.免费观看| 亚洲国产高清在线一区二区三| 久久久久国内视频| 午夜两性在线视频| 制服诱惑二区| 色哟哟哟哟哟哟| 18禁裸乳无遮挡免费网站照片| 又紧又爽又黄一区二区| 高清毛片免费观看视频网站| 精品国产亚洲在线| 香蕉国产在线看| 国产99白浆流出| 高清毛片免费观看视频网站| 老汉色∧v一级毛片| a在线观看视频网站| av福利片在线观看| 国产精品 国内视频| 老熟妇乱子伦视频在线观看| 久久精品成人免费网站| 成人特级黄色片久久久久久久| 午夜福利视频1000在线观看| 亚洲一区二区三区色噜噜| 禁无遮挡网站| 两个人的视频大全免费| 久久久精品国产亚洲av高清涩受| 亚洲精品一区av在线观看| xxxwww97欧美| 亚洲美女黄片视频| 校园春色视频在线观看| 久久精品夜夜夜夜夜久久蜜豆 | 在线视频色国产色| 成年女人毛片免费观看观看9| 久久久国产欧美日韩av| 国产精品亚洲av一区麻豆| 亚洲国产精品sss在线观看| 又爽又黄无遮挡网站| 亚洲成人中文字幕在线播放| 国产精品久久电影中文字幕| 宅男免费午夜| 黑人欧美特级aaaaaa片| 哪里可以看免费的av片| 免费一级毛片在线播放高清视频| 久久久久久大精品| 欧美乱码精品一区二区三区| 亚洲av熟女| 特级一级黄色大片| 国产成人精品久久二区二区91| 精品福利观看| 久久久久国内视频| 每晚都被弄得嗷嗷叫到高潮| 午夜精品久久久久久毛片777| 亚洲全国av大片| 三级毛片av免费| 国产三级在线视频| 成人三级做爰电影| 国产精品一及| 国产99久久九九免费精品| 欧美一区二区国产精品久久精品 | 国产欧美日韩精品亚洲av| 国产99久久九九免费精品| 亚洲av日韩精品久久久久久密| 可以在线观看毛片的网站| 九九热线精品视视频播放| 亚洲成av人片在线播放无| 国产精品av久久久久免费| 亚洲专区字幕在线| 日本a在线网址| 老熟妇乱子伦视频在线观看| 日韩大码丰满熟妇| 老司机靠b影院| 久久香蕉激情| 亚洲美女黄片视频| 99热这里只有精品一区 | 久久久久久久午夜电影| 亚洲午夜理论影院| 99国产精品一区二区蜜桃av| 国产亚洲av高清不卡| 真人一进一出gif抽搐免费| 99久久久亚洲精品蜜臀av| 99热6这里只有精品| 午夜免费成人在线视频| 精品久久久久久成人av| 亚洲,欧美精品.| 窝窝影院91人妻| 露出奶头的视频| 国产亚洲精品一区二区www| 亚洲欧美一区二区三区黑人| 国产亚洲av高清不卡| 一本一本综合久久| 女人高潮潮喷娇喘18禁视频| 欧美另类亚洲清纯唯美| 日韩欧美三级三区| 一级毛片高清免费大全| 午夜亚洲福利在线播放| 国产精品免费视频内射| 精品欧美国产一区二区三| 天天躁夜夜躁狠狠躁躁| 精品欧美一区二区三区在线| av中文乱码字幕在线| 女人被狂操c到高潮| 国产一区在线观看成人免费| 九色国产91popny在线| 九色成人免费人妻av| 亚洲一区二区三区不卡视频| 亚洲av熟女| 成人特级黄色片久久久久久久| 别揉我奶头~嗯~啊~动态视频| 老汉色∧v一级毛片| 别揉我奶头~嗯~啊~动态视频| 神马国产精品三级电影在线观看 | 精品乱码久久久久久99久播| 丁香六月欧美| 国产伦人伦偷精品视频| 一边摸一边做爽爽视频免费| 免费在线观看黄色视频的| 少妇人妻一区二区三区视频| 91大片在线观看| 亚洲精品粉嫩美女一区| 99国产精品一区二区三区| 日韩大码丰满熟妇| 亚洲 国产 在线| 特大巨黑吊av在线直播| 免费在线观看完整版高清| 亚洲中文日韩欧美视频| 久久久久久久精品吃奶| 两个人的视频大全免费| 欧美3d第一页| 黄片小视频在线播放| 99国产精品99久久久久| av视频在线观看入口| 一边摸一边做爽爽视频免费| 国产麻豆成人av免费视频| 欧美在线黄色| 九色国产91popny在线| a级毛片a级免费在线| 国内精品一区二区在线观看| 制服诱惑二区| 色在线成人网| 最新美女视频免费是黄的| 久久久久久国产a免费观看| 日韩国内少妇激情av| www.www免费av| 男人舔奶头视频| 成熟少妇高潮喷水视频| 深夜精品福利| 国产成人精品久久二区二区免费| 国产精品久久久久久人妻精品电影| 精品国产亚洲在线| 国产亚洲欧美98| av欧美777| 国产精品电影一区二区三区| 久久中文字幕一级| 亚洲国产高清在线一区二区三| 国产成人av教育| 日本 av在线| 看免费av毛片| 亚洲av熟女| 免费在线观看影片大全网站| 狂野欧美激情性xxxx| 欧美午夜高清在线| 色综合婷婷激情| a级毛片在线看网站| 99久久久亚洲精品蜜臀av| 国产v大片淫在线免费观看| 宅男免费午夜| 欧美乱码精品一区二区三区| 中国美女看黄片| 波多野结衣高清无吗| 校园春色视频在线观看| 久久香蕉国产精品| 天天一区二区日本电影三级| 久9热在线精品视频| 五月伊人婷婷丁香| 久久久精品大字幕| 免费观看人在逋| 午夜两性在线视频| 女人被狂操c到高潮| 久久中文看片网| 中文字幕av在线有码专区| 啪啪无遮挡十八禁网站| 少妇粗大呻吟视频| 色av中文字幕| 琪琪午夜伦伦电影理论片6080| 国内精品一区二区在线观看| 成人av在线播放网站| 搡老岳熟女国产| 国产探花在线观看一区二区| 日韩av在线大香蕉| 午夜福利高清视频| 亚洲男人的天堂狠狠| 日韩三级视频一区二区三区| 老熟妇乱子伦视频在线观看| 在线观看免费午夜福利视频| 一区福利在线观看| 天堂av国产一区二区熟女人妻 | 日韩国内少妇激情av| 黄片大片在线免费观看| 国产亚洲精品第一综合不卡| 91老司机精品| 国产成人精品久久二区二区91| 黄色 视频免费看| 欧美另类亚洲清纯唯美| 国产三级黄色录像| 国产精品98久久久久久宅男小说| 黄色片一级片一级黄色片| 国产精品久久久人人做人人爽| 看片在线看免费视频| 日韩av在线大香蕉| 天天躁夜夜躁狠狠躁躁| 精品久久久久久久久久久久久| 国产精品av久久久久免费| 全区人妻精品视频| 可以免费在线观看a视频的电影网站| 岛国视频午夜一区免费看| 亚洲va日本ⅴa欧美va伊人久久| 一本一本综合久久| 在线观看一区二区三区| 日日摸夜夜添夜夜添小说| 中亚洲国语对白在线视频| 人人妻,人人澡人人爽秒播| 国产片内射在线| 最近视频中文字幕2019在线8| 久热爱精品视频在线9| 成年免费大片在线观看| 欧美黑人欧美精品刺激| 国产精品一区二区三区四区免费观看 | 久久久久久久久久黄片| 熟妇人妻久久中文字幕3abv| 午夜精品久久久久久毛片777| 午夜a级毛片| 9191精品国产免费久久| 桃红色精品国产亚洲av| 美女午夜性视频免费| 丁香六月欧美| 日韩高清综合在线| 在线视频色国产色| 精品国内亚洲2022精品成人| 色精品久久人妻99蜜桃| 最好的美女福利视频网| 精品国内亚洲2022精品成人| 久久亚洲真实| 神马国产精品三级电影在线观看 | 久久人妻福利社区极品人妻图片| 动漫黄色视频在线观看| 精品久久蜜臀av无| 欧美一区二区国产精品久久精品 | 99国产精品一区二区蜜桃av| 伊人久久大香线蕉亚洲五| 成人18禁高潮啪啪吃奶动态图| 性色av乱码一区二区三区2| 久久久久久九九精品二区国产 | 一个人免费在线观看的高清视频| 午夜两性在线视频| 国产v大片淫在线免费观看| 色综合站精品国产| 国产视频一区二区在线看| 欧美成人免费av一区二区三区| 亚洲中文av在线| 亚洲人成网站在线播放欧美日韩| 欧美一级毛片孕妇| 亚洲国产欧美人成| 一区二区三区激情视频| 老司机午夜福利在线观看视频| 亚洲无线在线观看|