• <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 ?

    Sources of Particular Pollutants in Ambient Air at a Petrochemical Enterprise

    2013-07-31 23:13:35XueJianliangZhaoDongfengChengJianguangChenLuLiuWei
    中國(guó)煉油與石油化工 2013年4期

    Xue Jianliang; Zhao Dongfeng; Cheng Jianguang; Chen Lu; Liu Wei

    (1. College of Chemical and Enνironmental Engineering, Shandong Uniνersity of Science and Technology, Qingdao, Shandong 266590; 2.College of Chemical Engineering, China Uniνersity of Petroleum(East China), Qingdao, Shandong 266580)

    Sources of Particular Pollutants in Ambient Air at a Petrochemical Enterprise

    Xue Jianliang1,2; Zhao Dongfeng2; Cheng Jianguang1; Chen Lu2; Liu Wei2

    (1. College of Chemical and Enνironmental Engineering, Shandong Uniνersity of Science and Technology, Qingdao, Shandong 266590; 2.College of Chemical Engineering, China Uniνersity of Petroleum(East China), Qingdao, Shandong 266580)

    The study on source apportionment of particular pollutants in ambient air at a petrochemical enterprise is the basis of the control over air pollution. Through analyzing particular pollutants in the samples collected from one petrochemical enterprise in northwestern China, the sources of particular pollutants were discussed. The test results showed that concentrations of particular pollutants in different sites were remarkably different. Results showed that the sampling sites with higher concentrations of particular pollutants, including toluene, xylenes, NH3and H2S, were located at the boundary of the petrochemical enterprise. Instead, the concentrations of NMHC in the ambient air sampling sites were higher than those at the boundary of the petrochemical enterprise. The sampling sites with higher concentrations of particular pollutants were located in the area that was close to the petrochemical enterprise. The results obtained from the Pearson correlation coefficients analyses, the factor analyses, andχ2-tests of the particular pollutants had revealed that NH3, H2S, toluene and xylenes at all sampling sites came from the same source, while NMHC might come from some other sources besides the petrochemical enterprise.

    particular pollutants; sources apportionment; Pearson correlation coefficient

    1 Introduction

    Following the accelerated process of industrialization in China, the air pollutants discharged from the industrial enterprises have greatly affected the people’s health[1-2]. Among these air pollutants, the benzene homologues (viz.: benzene, toluene, ethylbenzene and xylenes), the nonmethane hydrocarbons (NMHC), ammonia, and hydrogen sulfide are particular environmental pollutants emanating from petroleum and petrochemical industries[3-6]. These pollutants have brought forth some negative impact, such as poor air visibility and other health problems[4,7]. For example, the benzene homologues are toxic compounds and some of them are known as carcinogens[8]. However, NMHC are important chemicals taking part in the photochemical processes in the troposphere[9]. Furthermore, during the photochemical process, these particular environmental pollutants can react with each other to form secondary pollutants[10].

    Recently, many researches have been focusing on monitoring the concentration or characteristics of air pollutants in some regions. While a few related study worked on the contribution of some specific emissions of particular pollutants from petrochemical enterprises. In this paper, some correlation methods were carried out to analyze the correlation between samples collected from the petrochemical enterprise and those collected around a typical petrochemical enterprise. The results could provide some qualitative analyses about the contribution of petrochemical enterprise to the particular pollutants.

    2 Experimental

    2.1 The selected particular pollutants of petrochemical enterprise and their standardized analytical methods

    The particular pollutants of the petrochemical enterprise (e.g. NMHC, benzene homologues, ammonia, and hydrogen sulfide) were analyzed. Concentrations of these pol-lutants were monitored in order to verify the contribution of the petrochemical enterprise to the pollution of ambient air. Each monitoring item and their standardized analytical methods are shown in Table 1.

    Table 1 Items monitored and their standard analytical methods

    2.2 The specified sampling sites

    The target petrochemical enterprise is situated in northwestern China. According to the local meteorological information, this research chose 11 monitoring sites around the petrochemical enterprise. All the 11 monitoring sites are listed in Table 2, with each site showing its relative distance to the centre and its direction to the petrochemical enterprise. The petrochemical enterprise is located in a vast plain. And, there is no other industrial enterprises except the said petrochemical enterprise in the surrounding.

    This research used the samples collected at the border of the petrochemical enterprise to study the concentrations of pollutant sources. According to the pertaining rule, this research had chosen four sites as the pollutant sources of the petrochemical enterprise.

    2.3 Quality control and quality assurance

    The concentrations of pollutants at the eleven monitoring sites could represent the pollutant concentrations of the area. In the process of monitoring, the sampling was strictly performed in accordance with the relevant standards, and the pollutant quantification was performed using the five-point calibration approach. The blank test was also adopted. And the analytical methods did not find detectable amounts of the target analytes. The measured concentrations of the pollutants stipulated in the National Institute of Standards and Technology (NIST) 1941 were between 90% to 116% of the specified values. Therefore, the average recoveries varied from 85% to 104%.

    Table 2 Location of sites for monitoring atmospheric particulate matter and their relative direction to the petrochemical enterprise

    3 Results and Discussion

    3.1 Distribution of the particular pollutants

    All the samples of particular pollutants at 11 sampling sites around the petrochemical enterprise were collected. The mass concentrations of pollutants are shown in Table 3.

    Table 3 Mass concentrations of specific pollutants collected at sampling sites of petrochemical enterprisemg/m3

    Table 3 shows that the concentrations of particular pollutants at different sampling sites were significantly different. Results showed that the sampling sites with higher concentrations of the particular pollutants, such as toluene, xylenes, NH3and H2S, were located at the boundary of the petrochemical enterprise. For example, the highest concentration of toluene, xylenes, NH3and H2S was 4.89, 4.21, 0.13, and 0.013 mg/m3, respectively. Particularly, the concentration of toluene, xylenes and H2S at the boundary of petrochemical enterprise could be 10 times more than their respective concentration at the ambient air sampling sites. Instead, the concentration of NMHC at ambient air sampling sites was higher than that at the boundary of petrochemical enterprise.

    To study the spatial distribution of these specific pollutants at the ambient air sampling sites, Table 3 also indicates that the sampling sites with higher concentration of these specific pollutants were located in areas that were near the petrochemical enterprise. Taking the sampling sites #1 and #3 as the examples, it could be seen that the mass concentration of NMHC, toluene, xylenes, NH3and H2S at the sampling site #1 was 3.86, 0.162, 0.17, 0.13, and 0.008 mg/m3, respectively. Whereas the concentration of these related pollutants at the sampling site #3 was only 3.72, 0.188, 0.179, 0.12, and 0.005 mg/m3, respectively.

    3.2 Further analyses on sources of particular pollutants

    The application of a statistical study would be helpful to identification of the sources of particular pollutants in order to shed light on the correlation between the concentrations of the pollutants. This paper applied the Principal Component Analysis to find out the most important components inside, and then rotated the factors with the Varimax rotation method in an attempt to find a factor solution that was equal to that obtained in the initial extraction and would have simpler and more explicit interpretation. Then, these rotated factors could reasonably interpret the possible sources of the ambient air pollution. Finally, theχ2-test was used to verify the previous results.

    (1) The Pearson Correlation Coefficients and Factor Analysis of specific pollutants

    To further investigate the sources of the particular pollutants, the Pearson Correlation Coefficient was adopted to carry out the correlation analyses[10]. In statistics, the Pearson Correlation Coefficient can reflect the relationship between 2 variables, e.g.: 0<|rp|≤0.2 indicates a weak correlation or no correlation; 0.2<|rp|≤0.4 indicates a low correlation; 0.4<|rp|≤0.6 indicates a medium correlation; 0.6<|rp|≤0.8 indicates a significant correlation; and 0.8<|rp|<1 indicates a high correlation. The formula of Pearson Correlation Coefficient is as follows:

    in whichXandYare two different variables, andkis the number of samples.

    The Pearson Correlation Coefficients of particular pollutant concentrations are presented in Table 4, and the factor loading graph of particular pollutant is depicted in Table 5.

    Table 4 Pearson Correlation Coefficients of specific pollutants collected at ambient sampling sites and at boundary of petrochemi

    It can be seen from Table 4 that the Pearson concentration correlation of 4 pollutants was 0.901, which meant a significant correlation. The result showed that NH3, H2S, toluene and xylenes in all sampling sites came from the same source. Upon considering the industrial enterprises besides the target petrochemical enterprise, the petrochemical enterprise was considered as the only source for emission of NH3, H2S, toluene and xylenes.

    However, the Pearson Correlation Coefficient fell down to 0.593 when NMHC was included. Thus it could be inferred that there were many other NMHC sources besides the petrochemical enterprise. As for the concentration correlation of the particular pollutants at the ambient sampling sites and at the boundary of petrochemical enterprise, the rest four pollutants except NMHC as a subset could be better inferred as the source.

    It can be seen from Table 5 that the loading values on each factor have been polarized and became more responsive. The loading of Component 1 on NH3, and H2S were 0.833 and 0.870, respectively, which were much higherthan that on NMHC. Since previous results showed that NH3, and H2S had a high correlation, thus these 2 points could work together to con firm that they might come from the same source (the target petrochemical enterprise). According to the manufacturing process of the petrochemical enterprise, and by analyzing the emission sources of the petrochemical enterprise, it could be inferred that they were probably originated from the wastewater treatment plant in the petrochemical enterprise.

    Table 5 The factor loading graph of specific pollutan

    Similarly, the component 2 had high loading on benzene and methylbenzene, which were 0.714 and 0.790, respectively. Since previous results also showed that there was a high correlation between toluene and xylenes, it could also prove that they might come from the petrochemical enterprise. And through further analyses on the manufacturing process of petrochemical enterprise, it was verified that benzene and methylbenzene might come from the catalytic reforming unit or the gasoline pyrolysis equipment.

    Component 3 had high loading on NMHC, which was equal to 0.677. Based on the previous analyses, it could be inferred that the petrochemical enterprise was not its sole source and there might be some other sources that had contributed to the air pollution.

    In summary, NH3, H2S, toluene and xylenes were probably emanated from petrochemical enterprise. NH3and H2S mainly came from wastewater treatment plant, while toluene and xylenes could be originated from the catalytic reforming unit, the naphtha pyrolysis unit, and the fractionation unit along with the fugitive emission sources at the petrochemical enterprise.

    (2)χ2-test

    The values of χ2-test is shown in Table 6, wherepis the difference correlation between two specific pollutants. The valuep≥0.05 indicates that the difference between two specific pollutants is not significant. Instead, the valuep<0.05 indicates that the difference between two specific pollutants is significant.

    Table 6 Values ofχ2-test among 5 specific pollutants at the ambient air sampling sites

    It has been shown in Table 6 that the values ofχ2-test between NH3, H2S, toluene and xylenes were all ≥0.05, that is to say, the sources of NH3, H2S, toluene and xylenes are the same. The values were significantly different between NMHC and other components, thus NMHC could come from other sources. This is the reason why the concentration of NMHC at ambient air sampling sites was higher than that at the boundary of petrochemical enterprise.

    4 Conclusions

    By analyzing the concentration characteristics of particular pollutants and their correlation, as well as by applying the Principal Component Analysis and the Factor Analysis to the study on the source of particular air pollutants, the following conclusions could be drawn up:

    (1) Concentrations of particular pollutants in different sites were significantly different. Results showed that the sampling sites with higher concentrations of particular pollutants, such as toluene, xylenes, NH3and H2S, were located at the boundary of the petrochemical enterprise. Instead, the concentrations of NMHC at ambient air sampling sites were higher than those at the boundary of petrochemical enterprise.

    (2) The sampling sites with higher concentrations of particular pollutants were located in the area near the petrochemical enterprise.

    (3) Application of the statistical study would be helpful to the analysis on the source of the specific pollutants to shed light on the correlation of the concentrations of the pollutants. By means of the Pearson Correlation Coefficients, the Factor Analysis, and theχ2-test of specific pollutants, the results showed that NH3, H2S, toluene and xylenes, which were collected at all sampling sites, camefrom the same sources and NMHC could come from other sources besides the petrochemical enterprise.

    Acknowledgments:This study was financially supported by the Fundamental Research Funds for the Central Universities (No. 13CX06055A), and Key Technology Development Projects of Qingdao Economic and Technological Development Zone (No. 2013-1-58).

    [1] Chameides W L, Fehsenfeld F, Rodgers M O, et al. Ozone precursor relationships in the ambient air[J]. Journal of Geophysical Research: Atmospheres, 1992, 97(D5): 6037-6055

    [2] Kniemeyer O, Fischer T, Wilkes H, et al. Anaerobic degradation of ethylbenzene by a new type of marine sulfate-reducing bacterium[J]. Appl Environ Microbiol, 2003, 69(2): 760-768

    [3] Li He, Liu Yu H, Luo Na, et al. Biodegradation of benzene and its derivatives by a psychrotolerant and moderately haloalkaliphilicPlanococcussp. strain ZD22[J]. Research in Microbiology, 2006, 157(7): 629-636

    [4] Prenafeta-Boldu F X, Vervoort J, Grotenhuis J T C, et al. Substrate interactions during the biodegradation of benzene, toluene, ethylbenzene, and xylene (BTEX) hydrocarbons by the fungusCladophialophorasp. strain T1[J]. Appl Environ Microbiol, 2002, 68(6): 2660-2665

    [5] M?llmann-Coers M, Klemp D, Mannschreck K, et al. Statistical study of the diurnal variation of modeled and measured NMHC contributions[J]. Atmospheric Environment, 2002, 36(S1): 109-122

    [6] Zervas E, Montagne X, Lahaye J. The influence of gasoline formulation on specific pollutant emissions[J]. Journal of the Air & Waste Management Association, 2011, 49(11): 1304-1314

    [7] Abdulkareem A S. Urban air pollution evaluation by computer simulation: A case study of petroleum refining company in Nigeria[J]. Leonardo Journal of Sciences, 2006, 4(6): 17-28

    [8] Rooney-Varga J N, Anderson R T, Fraga J L, et al. Microbial communities associated with anaerobic benzene degradation in a petroleum-contaminated aquifer[J]. Appl Environ Microbiol, 1999, 65(7): 3056-3063

    [9] Rappenglü Ck B, Fabian P, Kalabokas P, et al. Quasi-continuous measurements of non-methane hydrocarbons (NMHC) in the Greater Athens area during medcaphot-trace[J]. Atmospheric Environment, 1998, 32(12): 2103-2121

    [10] Miyuki Noguchi, Mun-joo Bae, Kyoko Yamashita, et al. Correlation of the ratio of non-methane hydrocarbon and nitrogen oxide concentrations in the atmosphere and outdoor environment[J]. Building and Environment, 2009, 44(7): 1489-1492

    Recieved date: 2013-08-25; Accepted date: 2013-11-03.

    Xue Jianliang, E-mail: ll-1382@163.com.

    亚洲国产欧美网| 中文字幕最新亚洲高清| 在线观看免费日韩欧美大片| 各种免费的搞黄视频| 自拍欧美九色日韩亚洲蝌蚪91| 人人妻人人添人人爽欧美一区卜| 黄色怎么调成土黄色| netflix在线观看网站| 麻豆精品久久久久久蜜桃| 中文字幕制服av| 亚洲av在线观看美女高潮| 国产黄色视频一区二区在线观看| 9191精品国产免费久久| 国产成人a∨麻豆精品| 久久ye,这里只有精品| 制服人妻中文乱码| 亚洲成人手机| 国产99久久九九免费精品| 黄色毛片三级朝国网站| 欧美另类一区| 国产亚洲欧美精品永久| 国产麻豆69| 在线观看免费午夜福利视频| 伊人亚洲综合成人网| 在线天堂最新版资源| 国产成人一区二区在线| 欧美最新免费一区二区三区| 最黄视频免费看| 亚洲av电影在线观看一区二区三区| 欧美日韩精品网址| 日韩欧美一区视频在线观看| 久久久亚洲精品成人影院| 国产一区亚洲一区在线观看| 高清欧美精品videossex| 十八禁高潮呻吟视频| 九草在线视频观看| 91国产中文字幕| 亚洲精品国产色婷婷电影| 亚洲成色77777| 欧美日韩成人在线一区二区| 成人漫画全彩无遮挡| 男人爽女人下面视频在线观看| 亚洲成人免费av在线播放| 亚洲av电影在线进入| 视频区图区小说| 精品少妇久久久久久888优播| 天堂俺去俺来也www色官网| 考比视频在线观看| 国产精品国产三级专区第一集| 男女边吃奶边做爰视频| 亚洲欧美日韩另类电影网站| 国产毛片在线视频| av免费观看日本| 久久人人爽av亚洲精品天堂| 精品国产超薄肉色丝袜足j| 国产一卡二卡三卡精品 | 欧美中文综合在线视频| 在现免费观看毛片| 人妻 亚洲 视频| 母亲3免费完整高清在线观看| 色综合欧美亚洲国产小说| 高清欧美精品videossex| 欧美av亚洲av综合av国产av | 亚洲精品第二区| 午夜福利一区二区在线看| 在线看a的网站| av又黄又爽大尺度在线免费看| 亚洲自偷自拍图片 自拍| 少妇精品久久久久久久| 母亲3免费完整高清在线观看| 免费久久久久久久精品成人欧美视频| 久热爱精品视频在线9| 考比视频在线观看| 国产黄频视频在线观看| 欧美日韩视频高清一区二区三区二| 青春草国产在线视频| 久久天堂一区二区三区四区| 亚洲av国产av综合av卡| 观看美女的网站| 国产精品久久久久久精品古装| 高清视频免费观看一区二区| 成人国产麻豆网| 王馨瑶露胸无遮挡在线观看| 国产成人系列免费观看| 国产精品 国内视频| 伦理电影免费视频| 欧美日韩亚洲高清精品| 国产av精品麻豆| 七月丁香在线播放| 99九九在线精品视频| 日日啪夜夜爽| 人妻一区二区av| 国产成人系列免费观看| 成人18禁高潮啪啪吃奶动态图| 久久久久久久久免费视频了| 久久影院123| 亚洲一卡2卡3卡4卡5卡精品中文| 久久久久久免费高清国产稀缺| 国产精品久久久久久精品电影小说| 国产精品偷伦视频观看了| 午夜av观看不卡| 人体艺术视频欧美日本| 免费黄网站久久成人精品| a 毛片基地| 丝袜美足系列| 又黄又粗又硬又大视频| 亚洲情色 制服丝袜| 曰老女人黄片| 自线自在国产av| h视频一区二区三区| 亚洲精品久久成人aⅴ小说| 蜜桃在线观看..| av有码第一页| 高清黄色对白视频在线免费看| 大香蕉久久成人网| 久久久精品国产亚洲av高清涩受| 国产精品免费大片| 青青草视频在线视频观看| netflix在线观看网站| 777久久人妻少妇嫩草av网站| 999精品在线视频| 久久久久久人妻| 少妇精品久久久久久久| 热99久久久久精品小说推荐| 久久天堂一区二区三区四区| 五月天丁香电影| 777久久人妻少妇嫩草av网站| 日日啪夜夜爽| 久久精品aⅴ一区二区三区四区| 国产97色在线日韩免费| 国产极品粉嫩免费观看在线| 狂野欧美激情性xxxx| 亚洲综合色网址| 久久久久久久精品精品| 精品少妇内射三级| 婷婷色综合www| 性色av一级| 欧美日本中文国产一区发布| 可以免费在线观看a视频的电影网站 | 免费观看a级毛片全部| 欧美日韩福利视频一区二区| 久久国产精品男人的天堂亚洲| 国产在线一区二区三区精| 在线亚洲精品国产二区图片欧美| 亚洲国产毛片av蜜桃av| 国产不卡av网站在线观看| 精品少妇黑人巨大在线播放| 中文字幕另类日韩欧美亚洲嫩草| 国产极品天堂在线| 国产亚洲一区二区精品| 丝瓜视频免费看黄片| 国产日韩欧美在线精品| 国产精品国产av在线观看| 美女高潮到喷水免费观看| 国产精品久久久久久人妻精品电影 | 成人亚洲欧美一区二区av| 国产精品亚洲av一区麻豆 | 午夜av观看不卡| 在线观看免费高清a一片| 高清在线视频一区二区三区| 国产极品天堂在线| 天天躁日日躁夜夜躁夜夜| 免费黄频网站在线观看国产| 一本一本久久a久久精品综合妖精| 天天躁日日躁夜夜躁夜夜| 久久97久久精品| 热99国产精品久久久久久7| 一边摸一边做爽爽视频免费| 亚洲av在线观看美女高潮| 久久久欧美国产精品| 成年美女黄网站色视频大全免费| 狠狠婷婷综合久久久久久88av| 免费高清在线观看视频在线观看| 亚洲国产av新网站| 久久久精品94久久精品| 亚洲四区av| 亚洲精品国产av蜜桃| 国产色婷婷99| 九草在线视频观看| 亚洲激情五月婷婷啪啪| 国产国语露脸激情在线看| 自拍欧美九色日韩亚洲蝌蚪91| 亚洲,一卡二卡三卡| 一级毛片我不卡| 国产欧美日韩一区二区三区在线| 亚洲第一青青草原| 99香蕉大伊视频| 日韩免费高清中文字幕av| 人妻 亚洲 视频| av福利片在线| 9热在线视频观看99| 一本一本久久a久久精品综合妖精| 日本vs欧美在线观看视频| 国产 精品1| 国产欧美亚洲国产| 精品久久蜜臀av无| 天天躁夜夜躁狠狠躁躁| 国产女主播在线喷水免费视频网站| 久久人人爽av亚洲精品天堂| 精品视频人人做人人爽| 亚洲欧美成人综合另类久久久| www日本在线高清视频| 亚洲视频免费观看视频| 狂野欧美激情性xxxx| 激情视频va一区二区三区| 精品国产一区二区三区久久久樱花| 亚洲国产中文字幕在线视频| 亚洲图色成人| av在线观看视频网站免费| 精品国产国语对白av| 久久精品aⅴ一区二区三区四区| av福利片在线| 国产精品免费视频内射| 丝袜美腿诱惑在线| 国产99久久九九免费精品| 国产一区有黄有色的免费视频| 汤姆久久久久久久影院中文字幕| 老司机深夜福利视频在线观看 | 一级a爱视频在线免费观看| av有码第一页| 国产片内射在线| 女人被躁到高潮嗷嗷叫费观| 亚洲激情五月婷婷啪啪| av不卡在线播放| 亚洲精品美女久久久久99蜜臀 | netflix在线观看网站| 久久毛片免费看一区二区三区| 亚洲国产av新网站| 老汉色∧v一级毛片| 国产免费福利视频在线观看| 精品少妇内射三级| 亚洲精品美女久久久久99蜜臀 | av女优亚洲男人天堂| 啦啦啦 在线观看视频| 在线观看三级黄色| 97在线人人人人妻| 18在线观看网站| 美国免费a级毛片| 国产毛片在线视频| 久久久精品94久久精品| 99热全是精品| 免费看不卡的av| 亚洲av日韩在线播放| 久久久久视频综合| 一级,二级,三级黄色视频| 国产熟女欧美一区二区| 少妇被粗大猛烈的视频| 看免费av毛片| 老汉色∧v一级毛片| 成年人免费黄色播放视频| 久久性视频一级片| 啦啦啦在线免费观看视频4| 纯流量卡能插随身wifi吗| 九草在线视频观看| av免费观看日本| 久久青草综合色| 久久久精品区二区三区| 亚洲av日韩精品久久久久久密 | 国产高清不卡午夜福利| 少妇人妻 视频| 高清av免费在线| 在线观看www视频免费| 亚洲久久久国产精品| av片东京热男人的天堂| 亚洲一区中文字幕在线| 国产av一区二区精品久久| 黄片无遮挡物在线观看| 亚洲欧美一区二区三区久久| 精品视频人人做人人爽| 哪个播放器可以免费观看大片| 久久国产亚洲av麻豆专区| 国产成人系列免费观看| 在线看a的网站| 菩萨蛮人人尽说江南好唐韦庄| 国产精品女同一区二区软件| 亚洲四区av| 成年美女黄网站色视频大全免费| 黑人巨大精品欧美一区二区蜜桃| 国产精品国产av在线观看| 色精品久久人妻99蜜桃| 国产高清国产精品国产三级| 久久久精品区二区三区| 午夜福利,免费看| 中文欧美无线码| 两个人看的免费小视频| 老司机靠b影院| 亚洲人成77777在线视频| 99久久精品国产亚洲精品| 久久 成人 亚洲| www.自偷自拍.com| 看免费成人av毛片| 中文字幕人妻熟女乱码| 制服人妻中文乱码| 午夜福利一区二区在线看| 国产精品亚洲av一区麻豆 | 两性夫妻黄色片| 欧美精品亚洲一区二区| 在线看a的网站| 亚洲婷婷狠狠爱综合网| 色94色欧美一区二区| 国产日韩一区二区三区精品不卡| 国产淫语在线视频| 大码成人一级视频| 波多野结衣av一区二区av| 成人黄色视频免费在线看| 男男h啪啪无遮挡| 免费少妇av软件| 色94色欧美一区二区| 欧美日韩福利视频一区二区| 一级毛片电影观看| 国产成人欧美| 天天添夜夜摸| 国产亚洲午夜精品一区二区久久| 建设人人有责人人尽责人人享有的| 日韩免费高清中文字幕av| 国产亚洲av片在线观看秒播厂| 大陆偷拍与自拍| 亚洲av男天堂| 99久久综合免费| 亚洲精品国产av蜜桃| 成人亚洲精品一区在线观看| 女人精品久久久久毛片| 欧美精品亚洲一区二区| 久久久久精品人妻al黑| 最新的欧美精品一区二区| √禁漫天堂资源中文www| 九色亚洲精品在线播放| 少妇被粗大的猛进出69影院| 欧美精品一区二区免费开放| 嫩草影院入口| 精品视频人人做人人爽| 人人妻人人澡人人看| 日韩 亚洲 欧美在线| 久久av网站| 777米奇影视久久| 秋霞在线观看毛片| 看免费成人av毛片| 夫妻午夜视频| 精品亚洲成a人片在线观看| 视频在线观看一区二区三区| 亚洲 欧美一区二区三区| 国产精品久久久av美女十八| 亚洲精品久久久久久婷婷小说| netflix在线观看网站| kizo精华| 视频区图区小说| 王馨瑶露胸无遮挡在线观看| 日韩一区二区视频免费看| 国产黄频视频在线观看| 高清不卡的av网站| 国产xxxxx性猛交| 91aial.com中文字幕在线观看| 久久人人爽人人片av| 男的添女的下面高潮视频| 2021少妇久久久久久久久久久| 人体艺术视频欧美日本| 免费在线观看视频国产中文字幕亚洲 | 午夜福利影视在线免费观看| 天堂中文最新版在线下载| 一区二区三区乱码不卡18| 老司机影院毛片| 午夜日韩欧美国产| 久久国产精品大桥未久av| 美女福利国产在线| 亚洲av日韩精品久久久久久密 | 欧美 亚洲 国产 日韩一| 国产有黄有色有爽视频| 欧美 亚洲 国产 日韩一| 免费观看av网站的网址| 男人爽女人下面视频在线观看| 在线看a的网站| 五月天丁香电影| 最近最新中文字幕大全免费视频 | 青春草视频在线免费观看| 日韩中文字幕视频在线看片| 少妇精品久久久久久久| 欧美日韩亚洲国产一区二区在线观看 | 免费看av在线观看网站| 在线观看免费日韩欧美大片| 美女视频免费永久观看网站| 日本一区二区免费在线视频| 伊人久久大香线蕉亚洲五| 亚洲欧洲国产日韩| 涩涩av久久男人的天堂| 精品午夜福利在线看| 国产色婷婷99| 一级毛片电影观看| 午夜福利,免费看| 国产成人av激情在线播放| 在线精品无人区一区二区三| 日本猛色少妇xxxxx猛交久久| 中文字幕制服av| 日韩av不卡免费在线播放| 中文字幕高清在线视频| 天天躁狠狠躁夜夜躁狠狠躁| 如日韩欧美国产精品一区二区三区| 国精品久久久久久国模美| av在线app专区| 十八禁人妻一区二区| 少妇猛男粗大的猛烈进出视频| 精品视频人人做人人爽| 亚洲欧美成人综合另类久久久| 水蜜桃什么品种好| 99国产精品免费福利视频| 精品国产乱码久久久久久小说| 在线 av 中文字幕| 亚洲男人天堂网一区| 夫妻午夜视频| 国产毛片在线视频| 亚洲精品久久午夜乱码| 黄色视频不卡| 人妻人人澡人人爽人人| 看免费成人av毛片| 国产一区二区 视频在线| 晚上一个人看的免费电影| 久久久久网色| 色94色欧美一区二区| 久久久国产一区二区| 18禁观看日本| 考比视频在线观看| 亚洲av男天堂| 男人爽女人下面视频在线观看| 免费女性裸体啪啪无遮挡网站| 午夜福利影视在线免费观看| 黑丝袜美女国产一区| 人人澡人人妻人| 国产xxxxx性猛交| 久久免费观看电影| 国产av国产精品国产| 免费少妇av软件| 日韩伦理黄色片| 一区二区三区激情视频| 亚洲激情五月婷婷啪啪| 亚洲精品国产av成人精品| 国产又爽黄色视频| 日韩精品有码人妻一区| 超碰成人久久| 亚洲国产日韩一区二区| 国产精品 欧美亚洲| 三上悠亚av全集在线观看| 亚洲精品自拍成人| 2021少妇久久久久久久久久久| www.av在线官网国产| 91老司机精品| 日本91视频免费播放| 国产欧美日韩综合在线一区二区| 日日爽夜夜爽网站| 国产成人午夜福利电影在线观看| 一级毛片 在线播放| 亚洲国产欧美日韩在线播放| 成人免费观看视频高清| 国产亚洲最大av| 欧美精品高潮呻吟av久久| 久久性视频一级片| 女的被弄到高潮叫床怎么办| 免费不卡黄色视频| 国产精品香港三级国产av潘金莲 | 亚洲精品av麻豆狂野| 色网站视频免费| 美女国产高潮福利片在线看| 一级,二级,三级黄色视频| 成年人午夜在线观看视频| kizo精华| 亚洲久久久国产精品| av又黄又爽大尺度在线免费看| 欧美日韩亚洲高清精品| 这个男人来自地球电影免费观看 | 涩涩av久久男人的天堂| 只有这里有精品99| 国产免费视频播放在线视频| 美女午夜性视频免费| 日韩av在线免费看完整版不卡| 久久精品久久精品一区二区三区| 无遮挡黄片免费观看| 日韩av在线免费看完整版不卡| 国产成人av激情在线播放| 丝瓜视频免费看黄片| 大话2 男鬼变身卡| 男男h啪啪无遮挡| avwww免费| 可以免费在线观看a视频的电影网站 | 国产成人一区二区在线| 亚洲欧洲日产国产| h视频一区二区三区| 中文精品一卡2卡3卡4更新| 日本91视频免费播放| 色婷婷av一区二区三区视频| 亚洲图色成人| 国产麻豆69| 久久久久久人妻| 别揉我奶头~嗯~啊~动态视频 | 亚洲欧美精品综合一区二区三区| 男女免费视频国产| 99久国产av精品国产电影| 人体艺术视频欧美日本| 久久综合国产亚洲精品| 热99久久久久精品小说推荐| 国产片内射在线| 亚洲,欧美精品.| 极品人妻少妇av视频| 老汉色∧v一级毛片| 免费观看av网站的网址| 美国免费a级毛片| 丝袜美腿诱惑在线| 免费观看性生交大片5| 蜜桃在线观看..| 男女边吃奶边做爰视频| 中文字幕亚洲精品专区| 纵有疾风起免费观看全集完整版| 日本欧美国产在线视频| 在线精品无人区一区二区三| 在线观看国产h片| 欧美人与善性xxx| 两个人看的免费小视频| 国产毛片在线视频| 丰满迷人的少妇在线观看| 亚洲国产精品999| 搡老乐熟女国产| 在线精品无人区一区二区三| 日日摸夜夜添夜夜爱| 在线天堂中文资源库| 卡戴珊不雅视频在线播放| 成人免费观看视频高清| 99久久99久久久精品蜜桃| 黄色视频不卡| 少妇猛男粗大的猛烈进出视频| 叶爱在线成人免费视频播放| 午夜免费鲁丝| 国产成人午夜福利电影在线观看| 国产男人的电影天堂91| 亚洲美女搞黄在线观看| 一区二区三区精品91| 亚洲一区中文字幕在线| 最新的欧美精品一区二区| 老汉色∧v一级毛片| 国产一区二区三区av在线| 亚洲欧美精品综合一区二区三区| 电影成人av| 久久精品亚洲熟妇少妇任你| 亚洲国产精品一区二区三区在线| 久久久久网色| 亚洲国产欧美一区二区综合| 久久久久国产精品人妻一区二区| 麻豆av在线久日| 青春草国产在线视频| 黄片无遮挡物在线观看| 午夜精品国产一区二区电影| 午夜老司机福利片| 伊人久久国产一区二区| 亚洲av成人精品一二三区| 国产乱来视频区| 亚洲色图 男人天堂 中文字幕| 女的被弄到高潮叫床怎么办| 免费人妻精品一区二区三区视频| 久久人人爽人人片av| 亚洲精品,欧美精品| 日韩中文字幕欧美一区二区 | 可以免费在线观看a视频的电影网站 | 国产97色在线日韩免费| 一本一本久久a久久精品综合妖精| 婷婷色综合www| 国产精品一国产av| 久久狼人影院| 91精品伊人久久大香线蕉| 亚洲激情五月婷婷啪啪| 极品少妇高潮喷水抽搐| 成人影院久久| 欧美激情高清一区二区三区 | 国产成人91sexporn| 亚洲第一青青草原| 日本欧美国产在线视频| 精品国产乱码久久久久久小说| 在线观看免费视频网站a站| 亚洲成人手机| 免费人妻精品一区二区三区视频| 少妇精品久久久久久久| 久久97久久精品| 色精品久久人妻99蜜桃| 涩涩av久久男人的天堂| 国产成人av激情在线播放| 国产福利在线免费观看视频| 嫩草影视91久久| 制服人妻中文乱码| 欧美xxⅹ黑人| 国产精品蜜桃在线观看| 亚洲欧洲日产国产| 久久精品国产综合久久久| 男女下面插进去视频免费观看| 亚洲熟女毛片儿| 视频区图区小说| 精品国产一区二区三区四区第35| 亚洲精品国产色婷婷电影| 亚洲精品美女久久久久99蜜臀 | 最近手机中文字幕大全| 国产精品无大码| 欧美97在线视频| 在线观看免费高清a一片| 1024视频免费在线观看| www.自偷自拍.com| 国产精品人妻久久久影院| 久久精品aⅴ一区二区三区四区| www.熟女人妻精品国产| 热99久久久久精品小说推荐| 91老司机精品| 国产成人一区二区在线| 日日爽夜夜爽网站| 九草在线视频观看| 亚洲成人手机| 亚洲欧美精品自产自拍| 久久久久国产精品人妻一区二区| 国产精品无大码| 嫩草影视91久久| 爱豆传媒免费全集在线观看| 两个人免费观看高清视频| 一二三四中文在线观看免费高清|