• <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 ?

    Interannual variation of nutrients along a transect across the Kuroshio and shelf area in the East China Sea over 40 years*

    2018-04-02 03:03:54HUYingying胡瑩英GUOXinyu郭新宇ZHAOLiang趙亮
    Journal of Oceanology and Limnology 2018年1期
    關鍵詞:趙亮

    HU Yingying (胡瑩英) GUO Xinyu (郭新宇) ZHAO Liang (趙亮)

    1 Center for Marine Environmental Studies, Ehime University, Matsuyama 7908577, Japan

    2 Key Laboratory of Marine Environment and Ecology, Ministry of Education, Ocean University of China, Qingdao 266100,China

    3 College of Environmental Science and Engineering, Ocean University of China, Qingdao 266100, China

    4 College of Marine and Environmental Sciences, Tianjin University of Science and Technology, Tianjin 300457, China

    1 INTRODUCTION

    Marginal seas of the Northwest Pacific Ocean exhibit high primary and secondary productivity,which is supported by high nutrient concentrations(Hama et al., 1997; Gong et al., 2003). These are generally important fishing grounds, and millions of people along the coasts make a living from the seas.However, fisheries cannot be maintained without new production, which relies upon external source of nutrients (Chen, 2008). Therefore, studies of spatialtemporal variations in nutrient concentration in the marginal seas of the North Pacific Ocean make significant contributions to both the shore-side ecosystem and the economy.

    The important role of nutrients in the ocean has spurred much attention from social and scientific standpoints, and much scientific research on nutrients in the ocean has been conducted starting several decades ago. Taking the East China Sea as an example,early research on nutrient concentration was mostly confined to riverine exports or to the estuaries and coastal areas (Lü et al., 1985; Huang et al., 1986; Hu et al., 1990). Wang (1991) produced a Marine Atlas,which is one of the most comprehensive reports on the spatial distribution of nutrients in the East China Sea, the Bohai Sea, and the Yellow Sea. Based on this atlas, Chen (2009) produced several maps of nutrient distributions (nitrate, phosphate and silicate) in the surface and bottom layers in summer and winter in the East China Sea with additional information from Korea, Taiwan and Japan.

    Although we have some fundamental information on the distribution of nutrients and seasonal variations,we have little information on long-term trends. There are only a few published reports that address this issue. Guo et al. (2012) used in-situ data from 88 cruises along transect PN from 1987 to 2009 and found an increasing nitrate concentration averaged along the transect. Lui et al. (2014) analyzed the same data and found that while nitrate and phosphate concentrations in the Kuroshio Intermediate Water(KIW) have increased, the dissolved oxygen (DO)concentration has decreased starting as early as 1982.Aoyama et al. (2008) found that nutrient concentration in the upper 200 m has been decreasing while dissolved oxygen content and sea water temperature have been increasing in the upper 200 m in the main stream of the Kuroshio in the East China Sea during the period of 1950 to 2004. Moreover, almost none of published reports examine interannual variation of nutrients.

    This study examines seasonal and interannual variation of temperature, salinity, DO, nitrate and phosphate levels from 1970 to 2013 along the transect in the East China Sea that is identified as section PN.Correlations between PDO and the other variables are made to find relationships in interannual variations between North Pacific Ocean and East China Sea.

    Table Locations and water depth at stations along section PN

    2 DATA AND METHOD

    Oceanographic and marine meteorological observation data from Japan Meteorological Agency(JMA) surveys conducted in the western North Pacific and in the seas adjacent to Japan by JMA research vessels from 1970 to 2013 were used in this study. In consideration of the study purpose, 11 stations along the classical PN section having locations and depths shown as Table 1 were chosen (Fig.1a).

    Surveys were conducted four times per year along section PN starting from April 1972, except for Stn. 3’and 4’ where observations were started from July 1977. From October 1996, observations at Stn. 7 to 9 were discontinued (Fig.1b).

    Most observations included measurements of water temperature, salinity, dissolved oxygen,phosphate, nitrate and chlorophyll a. We used temperature, salinity, dissolved oxygen, phosphate and nitrate in this study. Before further analysis of the data, several data processing steps were conducted to all parameters. Here we chose temperature as an example to explain the data processing procedure:

    1. Linear interpolation of data into standard levels.The observation data were not taken at exactly standard depths. So we used data at depths less than 10 m as surface data. And linear interpolated data to standard depths of 10 m, 20 m, 30 m, 50 m, 75 m,100 m, 125 m, 150 m, 200 m, 250 m, 300 m, 400 m,500 m, 600 m, 700 m and 800 m.

    2. Calculation of seasonal variation. All data from the same depth and collected in the same calendar month were averaged (pink line in Fig.2b).

    3. Seasonal variation correction. Monthly averages(Fig.2b) were subtracted from raw data (Fig.2a) from the same month. In Section 3.1, we used results in January, April, July and October from this procedure to represent spatial distributions of each parameter in winter, spring, summer and autumn.

    4. Annual variation correction. The average of monthly anomalies in the same year gives the annual average anomalies (pink line in Fig.2c).

    5. Smoothed averages (5-year smoothed averages)were calculated to evaluate long-term variation of annual average anomalies (pink line in Fig.2d).

    3 RESULT

    3.1 Spatial distributions of parameter values

    Seasonal variations of temperature and salinity(Fig.3a–h) are almost identical to the findings of Hinata (1996). In winter (Fig.3a), water temperature was vertically uniform due to strong mixing from Stn.5 to 9 on the continental shelf. A warm core corresponding to the Kuroshio was observed in layers shallower than 100 m from Stn. 2 to 4’. Compared to the mean water temperature during 1972 to 1993(Hinata, 1996), the 22°C isotherm expanded eastward to Stn. 2. In the layer deeper than 200 m from Stn. 2 to 4, the thermocline was slightly elevated toward the continental shelf. In spring, the water temperature was nearly the same as in winter in the surface layer on the continental shelf while it decreased considerably in the bottom layer (Fig.3b). In summer, a clear thermocline formed over the continental shelf(Fig.3c). Sea surface temperature was more than 28°C and showed less horizontal diff erence (Fig.3c)compared to in spring (Fig.3b) and winter (Fig.3a). In autumn, water temperature became vertically uniform in layers shallower than 50 m over the continental shelf due to the increase in vertical mixing (Fig.3d).As solar input decreased in autumn, sea surface temperature decreased compared to that in summer.

    Fig.1 a. map of study area showing station locations (filled circles) along section PN. Contours indicate isobaths of 50, 100 and 200 m; b. timing of temperature observations over the range of years

    Mean salinity along section PN is shown in Fig.3e–h. Salinity over the continental shelf was vertically uniform in winter when it exceeded 34, the maximum of the four seasons (Fig.3e). Maximum salinity occurred in layers between 100 and 250 m,which represent the Kuroshio subsurface water(Fig.3e). In spring, salinity on the continental shelf decreased due to the increase of river discharge and increase of precipitation (Fig.3f). In summer, salinity above the halocline was much lower compared to in winter and spring while salinity below the halocline was almost the same as that in other seasons (Fig.3g).In autumn, the eff ect of Changjiang diluted water was smaller, and salinity over the continental shelf increased compared to that with summer (Fig.3h).

    DO results (Fig.3i–l) also showed clear seasonal variation on both the continental shelf and Kuroshio region. DO was highest in spring on the continental shelf, especially at the surface (more than 260 μ mol/L)due to high primary production (Fig.3j). The second highest DO levels appeared in winter because of mixing and lower water temperature, which leads to higher saturated dissolved oxygen (Fig.3i). In deeperwater, DO decreases and is the lowest (<100 μ mol/L)at Stn. 3’ (depth, 800 m). Similar to distributions observed for water temperature and salinity, DO contours increased slightly toward the continental shelf.

    Fig.2 Temperature data with data processing

    For nitrate, higher concentrations were observed in winter on the shelf region (>1 μ mol/L, Fig.4a). As water temperature increases, production becomeshigher, and nitrate concentration in the euphotic layer decreases (Fig.4b). On the shelf bottom, high nitrate concentration is evident closer to the continental shelf than from the Kuroshio region. In spring, summer and autumn, the bottom water of the shelf had a higher nitrate concentration of 5–10 μ mol/L, which is larger than in the winter. In deeper water, nitrate increases and even exceeds 10 times that in the surface layer.

    Fig.3 Average values over 1973 to 2013 along section PN and depth for (a–d) temperature, (e–h) salinity, (i–l) DO in January(row 1), April (row 2), July (row 3) and October (row 4)

    Fig.4 Average values over 1973 to 2013 along section PN and depth for (a–d) nitrate, (e–h) phosphate, (i–l) AOU in January(row 1), April (row 2), July (row 3) and October (row 4)

    Spatial distribution of phosphate was similar to that of nitrate. Over the four seasons, shelf region(Stn. 6–9) had the highest phosphate concentration(0.25–0.5 μ mol/L) in winter, and shelf bottom water had the highest phosphate concentration (0.5–0.75 μ mol/L) in summer and autumn.

    Apparent oxygen utilization (AOU) is defined as the diff erence between O2' and O2, where O2' is the amount of oxygen the water would hold if it is in equilibrium with the atmosphere at the temperature and salinity of the water and O2is the dissolved oxygen actually measured in the water sample. AOU can represent how much dissolved oxygen respiration occurred in the water. Results show that a low value on the surface, which can be less than 0 μ mol/L, is a result of primary production being greater than consumption. There was no significant seasonal variation in the deep layers.

    Fig.5 Interannual variations of temperature along section PN by depth

    Fig.6 Interannual variations of salinity along section PN by depth

    3.2 Interannual variation

    Using 5-year smoothed averages for each parameter, interannual variations of each variable were examined at depths of 10, 50, 100, 200, 500 and 800 m in this study. Water temperature at depths of 10–200 m showed a similar pattern. Water was relatively warm around 1975 to 1980 and 1990 to 2005 while relatively cold in 1972, 1980 to 1990 and after 2008. Water temperature on the continental shelf showed a slightly diff erent pattern, especially around year 1985, when water temperature at 50 m at Stn. 9 reached a low value. Water temperature at 500 m was increasing before the late 1980s and decreasing after the late 1980s.

    The magnitude of interannual variation is represented by the standard deviation. Large interannual variation in water temperature was found at the surface (largest value, 0.44°C at 50 m at Stn. 9)and lowest (0.07°C) at 800 m at Stn. 3’.

    Interannual variation of salinity is shown in Fig.6.For depths shallower than 100 m, there were three high salinity periods around 1980, 1993 and 2004.Despite these three short high salinity periods, salinity showed an obvious increasing trend before 1993 and a decreasing trend after 1993. At deeper layers,changes in salinity showed diff erent patterns: at 500 m, increasing before 1985 and decreasing afterward;but at 800 m, a high in 1976 and a low in 1993 followed by an increasing trend. If we focus on the years after 2005, salinity in shallow layers was less than that at 100 m increasing slightly, while salinity in deeper layers (more than 200 m) was decreasing.

    The largest magnitude of interannual variation in salinity was found on the surface at Stn. 9 because this area can be influenced by Changjiang diluted water, which has a much lower salinity than Kuroshio water. At greater depths, the magnitude of the variation decreases and is at the smallest at 800 m.

    DO in Kuroshio surface and subsurface water was lowest around 1979, similar to the pattern of DO in surface water in the shelf region (Fig.7). DO increaseduntil 1990. In the bottom water of the shelf region(50 m at Stn. 7–9), DO anomalies suddenly decreased after 1988/1989 from +5 μ mol/L to -5 μ mol/s within 3 years, while at 50 m in Stn. 1–6, DO decreased slightly from 1990 to end of the 1990s. DO at 0–200 m was the highest around 2005, decreased from 2005 to 2010 and increased after the 2000s. From 200 to 800 m, the same pattern of high (1972) to low (1977)to high (1992/1993) to low (1998/1999) to high(2004) to low (2009) was observed. However, for long-term variation, an increasing trend was observed before 1992/1993 and decreased thereafter. The decreasing trend after 1992 was most obvious at 500 m as a ratio was around -0.43 μ mol/(L?yr).Similar results were also found in the North Pacific Intermediate Water (NPIW) by Takatani et al. (2012)as a particularly significant decreasing trend in DO after the mid-1980s with a ratio of (-0.36±0.08) μ mol/(kg?yr). This significant decreasing trend of DO in the NPIW is occurring a few years in advance of the trend observed here.

    Fig.7 Interannual variations of DO along section PN by depth

    The magnitude of interannual variation of DO was greatest at 500 m and smallest at 800 m (Fig.7), even though the spatial distribution of DO showed a lower value in deep layers than in shallow layers (Fig.3i–l).

    The nitrate dataset is the shortest available. Before 1985, only Stn. 1, 4 and 9 had nitrate observations and only twice per year. After 1996, no more observations were made at Stn. 7 to 9. From this limited data, we find that the nitrate concentration before 1985 was increasing but decreased from 1985 to 1989. After 1989, nitrate in the surface and subsurface water was not changing much, while nitrate at 500 m showed an increasing trend mean of 0.124 μ mol/(L?yr).

    The magnitude of nitrate variation (Fig.8) was much larger before 1989, and the diff erence in magnitude before and after 1989 is larger at shallow depths. At 500 m, the magnitudes before and after 1989 were similar to each other. After 1989, the nitrate concentration was tending to increase at 500 m, and the trend is most pronounced of the five depths.

    Phosphate observation was longer and more complete than for nitrate observation (Fig.9). Surface phosphate was high around 1982 and 2003 and low around 1990. After 1989, an interannual variation pattern similar to that of nitrate was observed at 500 m with an increasing trend mean of 0.005 1 μ mol/(L?yr).The magnitude of phosphate variation (Fig.9) was smallest for surface layers (0.01 μ mol/L at Stn. 4’ -0.022 μ mol/L at Stn. 5) and largest at 800 m(0.072 μ mol/L at Stn. 3’ -0.139 μ mol/L at Stn. 1).

    AOU at 200 m decreased from 1975 to 2003 and increased after 2004 (Fig.10). At 500 and 800 m,AOU showed a pattern of decreasing and then increasing. The diff erence is that the lowest value at 500 m appeared around 1992, while it appeared around 1988 at 800 m. At 800 m, AOU was even higher after 2010 than it was in 1975.

    4 DISCUSSION

    The hydrologic character along section PN section is determined by Kuroshio surface water, Kuroshio subsurface water, KIW, deep water, coastal water and mixed water.

    Figure 11 shows the correlations between variation at 200 m at Stn. 2 (represents Kuroshio subsurface water) and that at other depths and stations for each parameter. For DO, nitrate, phosphate and AOU, there is a significant positive correlation across almost the entire section. This suggests that DO, nitrate,phosphate and AOU show synchronous interannual variation in the Kuroshio subsurface water. However,water temperature in the surface and Kuroshio subsurface water ( T >14°C) shows an opposite pattern to that in the KIW ( T <14°C). Salinity variation shows an opposite pattern between shallower than 600 m and deeper than 600 m.

    From Fig.12 we can see that interannual variation of water temperature and salinity shows a positive relationship in the KIW and a negative relationship in Kuroshio surface and subsurface water. This means that when water temperature is high, salinity at the surface is low and salinity in the KIW is high, which leads to lighter water on the surface. The correlation between water temperature and the concentrations of nitrate, phosphate and DO matches well in Kuroshio intrusion water on the shelf slope. This is because when the intrusion is strong, intrusion water carries cold water with high nutrient and low DO to the shelf region.

    Trends in the long-term data sets show that nutrients in the KIW increased and DO decreased since as early as 1982 (Lui et al., 2014). As for interannual variation,we see results similar to those of Lui et al., (2014) if we set the study period from 1988 to 2010. For results prior to 1988, DO was increasing from 1973 to 1988 and phosphate was increasing before 1983 then decreasing from 1983 to 1988. This suggests that long-term trends might diff er, depending on the selected study period and that interannual variations of nitrate, phosphate and DO might be correlated to long-period variations.

    Fig.8 Interannual variations of nitrate along section PN by depth

    Most interannual variation can be explained by PDO(Fig.13). Water temperature is negatively correlated with PDO (R>-0.2 with a significant level ofP<0.1) at depths shallower than 300 m and a positively correlated(R>0.6 with a significant level ofP<0.1) at deeper depths. As for salinity, a positive correlation (R>0.8 with a significant level ofP<0.1) was found at depths shallower than 700 m and negative correlation was found at depths deeper than 700 m. We can find a significant positive correlation between PDO and phosphate as well as DO, a significant negative correlation between PDO and nitrate as well as AOU in the KIW and a portion of the bottom water of the shelf region.

    However, discharge of the Changjiang River cannot explain interannual variations along section PN very well (Fig.14). The first possible reason is that Changjiang diluted water is light and mainly flows in the shallow layers. The second reason is that the movement of Changjiang diluted water is mainly controlled by wind. Bai et al. (2014) studied summertime Changjiang River plume variation during 1998 to 2010 and found that the plume extension was more influenced by the southwesterly wind during periods of smaller discharge. The in fluence of Changjiang River to the area around the PN section should be considered to be a combination of nitrate concentration in water carried by Changjiang River, discharge from the Changjiang River and wind.

    From these results, we identi fied an interesting phenomenon. From the late 1980s and thereafter,water characteristics at 500 m all showed a trend diff erent than that at shallow depths. Temperature,salinity and DO decreased while phosphate, nitrate and AOU increased. At 500 m to 800 m, the KIW (Lui et al., 2014) has lower temperature, salinity, DO and higher phosphate, nitrate and AOU compared to at shallow depths. Lui et al. (2015) suggested that enhanced vertical movement of the seawater may be a cause of the increased AOU concentration but decreased DO concentration and θ in the KIW. Timedepth distribution of salinity at Stn. 3 (Fig.15) shows that the depth of upper boundary of KIW (S≤34.35) is becoming shallower after the late 1980s. A possible reason for this upward trend is the lower density of the NPIW (Kouketsu et al., 2009).

    Fig.9 Interannual variations of phosphate along section PN by depth

    Fig.10 Interannual variations of AOU along section PN by depth

    5 CONCLUSION

    This study describes the vertical patterns in temperature, salinity, DO, nitrate, phosphate and AOU along a transect (section PN) that crosses the Kuroshio in East China Sea. The characteristics of seasonal variation in temperature and salinity are almost consistent with the previous studies (Hinata,1996). DO in shallow layers shows seasonal variation with the highest value in spring and lowest value in autumn. Both nitrate and phosphate have a highest value in winter on the continental shelf region.Interannual variation of water temperatures and salinity changed diff erently between the Kuroshio surface water and KIW. In shallow layers, water temperature showed two relatively warm periods around 1975 to 1980 and 1990 to 2005 while other three periods are relatively cold. For depths shallower than 500 m, salinity increased to the highest value around 1993 and decreased thereafter. At 800 m, the lowest salinity was observed around 1993 and shows changes that are opposite to those at depths shallower than 500 m. For nutrients and DO from 200 to 800 m,all have a pattern of high (1972) to low (1977) to high (1992/1993) to low (1998/1999) to high (2004)to low (2009). For the long-term pattern of DO, an increasing trend was observed before 1992/1993 and decreasing one after that. Nitrate and phosphate were increasing up to 1985 and decreasing from 1985 to 1989. After 1992, DO at 500 m shows a significant decreasing trend because of the shallower upper boundary of KIW and is possibly related to a similar change of DO in NPIW. Conditions at the PN section are mainly controlled by the open ocean, and a good relationship is shown with the PDO index.Importantly, further research on the impact of interannual variation to ecosystem of East China Sea is necessary.

    Fig.11 Correlations coeffi cient with a significance level of P <0.1 (color) between a. temperature, b. salinity, c. DO, d. nitrate,e. phosphate, f. AOU at all observation points with the same variable at depth of 200 m of Stn. 2 (star)

    Fig.12 Correlations coeffi cient with a significance level of P <0.1 (color) between water temperature and a. salinity, b. DO, c.nitrate, d. phosphate, e. AOU at the same observation points

    Fig.13 Correlations coeffi cient with a significance level of P <0.1 (color) between PDO index and a. temperature, b. salinity,c. DO, d. nitrate, e. phosphate, f. AOU

    Fig.14 Correlations coeffi cient with a significance level of P <0.1 (color) between Changjiang discharge and a. temperature,b. salinity, c. DO, d. nitrate, e. phosphate, f. AOU

    6 ACKNOWLEDGEMENT

    HU Y. Y. thanks the China Scholarship Council(CSC) for supporting her stay in Japan.

    Aoyama M, Goto H, Kamiya H, Kaneko I, Kawae S, Kodama H, Konishi Y, Kusumoto K I, Miura H, Moriyama E,Murakami K, Nakano T, Nozaki F, Sasano D, Shimizu T,Suzuki H, Takatsuki Y, Toriyama A. 2008. Marine biogeochemical response to a rapid warming in the main stream of the Kuroshio in the western North Pacific.Fish.Oceanogr.,17(3): 206-218.

    Bai Y, He X Q, Pan D L, Chen C T A, Kang Y, Chen X Y, Cai W J. 2014. Summertime Changjiang River plume variation during 1998-2010.J.Geophys.Res.,119(9):6 238-6 257.

    Chen C T A. 2008. Distributions of nutrients in the East China Sea and the South China Sea connection.J.Oceanogr.,64(5): 737-751.

    Chen C T A. 2009. Chemical and physical fronts in the Bohai,Yellow and East China seas.J.Mar.Syst.,78(3): 394-410.

    Gong G C, Wen Y H, Wang B W, Liu G J. 2003. Seasonal variation of chlorophyllaconcentration, primary production and environmental conditions in the subtropical East China Sea.DeepSeaRes.IITop.Stud.Oceanogr.,50(6-7): 1 219-1 236.

    Guo X Y, Zhu X H, Wu Q S, Huang D J. 2012. The Kuroshio nutrient stream and its temporal variation in the East China Sea.J.Geophys.Res.,117(C1): C01026.

    Hama T, Shin K H, Handa N. 1997. Spatial variability in the primary productivity in the East China Sea and its adjacent waters.J.Oceanogr.,53(1): 41-51.

    Hinata T. 1996. Seasonal variation and long-term trends of the oceanographic conditions along a fixed hydrographic line crossing the Kuroshio in the East China Sea.Oceanogr.Mag.,45: 9-32.

    Hu M H, Yang Y P, Xu C L, Harrison P J. 1990. Phosphate limitation of phytoplankton growth in the Changjiang estuary.ActaOceanol.Sinica,9(3): 405-411.

    Huang S G, Yang J D, Ji W D, Yang X L, Chen G X. 1986.Spatial and temporal variation of reactive Si, N, P and their relationship in the Chang Jiang estuary water.Taiwan Strait,5(2): 114-123. (in Chinese with English abstract)

    Kouketsu S, Fukasawa M, Kaneko I, Kawano T, Uchida H,Doi T, Aoyama M, Murakami K. 2009. Changes in water properties and transports along 24°N in the North Pacific between 1985 and 2005.J.Geophys.Res.,114(C1):C01008.

    Lü X Q, Zhu C J, Zhang A B, Shi Z L. 1985. The characteristics of nutrient distribution in the southwest Bohai Sea and Huanghe River Estuary in summer.J.ShandongColl.Oceanol.,15(1): 146-158. (in Chinese with English abstract)

    Lui H K, Chen C T A, Lee J, Bai Y, He X Q. 2014. Looming hypoxia on outer shelves caused by reduced ventilation in the open oceans: case study of the East China Sea.Estuar.,Coast.ShelfSci.,151: 355-360.

    Lui H K, Chen C T A, Lee J, Wang S L, Gong G C, Bai Y, He X Q. 2015. Acidifying intermediate water accelerates the acidification of seawater on shelves: an example of the East China Sea.Cont.ShelfRes.,111: 223-233.

    Takatani Y, Sasano D, Nakano T, Midorikawa T, Ishii M. 2012.Decrease of dissolved oxygen after the mid-1980s in the western North Pacific subtropical gyre along the 137°E repeat section.GlobalBiogeochem.Cycles,26(2):GB2013.

    Wang Y H. 1991. Marine Atlas of Bohai Sea, Yellow Sea, East China Sea, Voloum 2: Chemistry. China Ocean Press,Beijing, China. 257p. (in Chinese)

    Fig.15 Time-depth distribution of salinity at Stn. 3 (colors represent salinity by 5-year moving average, black lines plot boundaries of KTW ( S ≥34.7) and KIW ( S ≤34.35)

    猜你喜歡
    趙亮
    虎子的周日
    十幾歲(2021年5期)2021-11-22 23:37:22
    Stable water droplets on composite structures formed by embedded water into fully hydroxylated β-cristobalite silica*
    守 候
    海燕(2020年9期)2020-11-23 01:54:27
    一個副總指揮的歧路人生
    檢察風云(2020年16期)2020-09-26 13:43:12
    鐵證如山
    故事會(2020年2期)2020-02-04 06:38:28
    A well-balanced positivity preserving two-dimensional shallow flow model with wetting and drying fronts over irregular topography *
    Simulating the responses of a low-trophic ecosystem in the East China Sea to decadal changes in nutrient load from the Changjiang (Yangtze) River*
    鬼破案
    鬼破案
    趙亮要給我介紹女朋友
    鴨綠江(2016年5期)2016-04-29 13:06:31
    亚洲国产精品专区欧美| 在线 av 中文字幕| 热re99久久精品国产66热6| 精品亚洲乱码少妇综合久久| www.av在线官网国产| 中文天堂在线官网| 亚洲色图综合在线观看| 99久国产av精品国产电影| 美女高潮的动态| 在线观看人妻少妇| 99视频精品全部免费 在线| 97人妻精品一区二区三区麻豆| 国产亚洲午夜精品一区二区久久 | 亚洲欧美精品自产自拍| 菩萨蛮人人尽说江南好唐韦庄| 久久综合国产亚洲精品| 秋霞在线观看毛片| 波多野结衣巨乳人妻| 大香蕉久久网| 免费观看av网站的网址| 国产伦在线观看视频一区| 亚洲内射少妇av| 少妇的逼好多水| 亚洲欧美日韩卡通动漫| 亚洲色图综合在线观看| 国产精品久久久久久av不卡| 午夜免费鲁丝| 欧美日韩视频高清一区二区三区二| 亚洲最大成人av| 日韩三级伦理在线观看| 亚洲精品国产色婷婷电影| 亚洲美女视频黄频| 日本-黄色视频高清免费观看| 美女脱内裤让男人舔精品视频| 成年版毛片免费区| 国产毛片a区久久久久| 伦理电影大哥的女人| 白带黄色成豆腐渣| 成人亚洲精品一区在线观看 | 男人狂女人下面高潮的视频| 国产精品久久久久久久久免| 国产在线一区二区三区精| 男女那种视频在线观看| 又爽又黄a免费视频| 别揉我奶头 嗯啊视频| 五月伊人婷婷丁香| av国产免费在线观看| 亚洲av成人精品一二三区| 一本—道久久a久久精品蜜桃钙片 精品乱码久久久久久99久播 | 日韩在线高清观看一区二区三区| h日本视频在线播放| 永久网站在线| 国产午夜精品久久久久久一区二区三区| av在线观看视频网站免费| 亚洲欧美精品专区久久| 看非洲黑人一级黄片| 亚洲av免费在线观看| 久久久精品欧美日韩精品| 69av精品久久久久久| 久久午夜福利片| 乱系列少妇在线播放| 久久人人爽人人爽人人片va| 国产成人91sexporn| 综合色av麻豆| 日本爱情动作片www.在线观看| 高清欧美精品videossex| 最近的中文字幕免费完整| 国产精品伦人一区二区| 熟妇人妻不卡中文字幕| 亚洲人成网站在线播| 亚洲精品一区蜜桃| 蜜桃久久精品国产亚洲av| 亚洲天堂国产精品一区在线| 新久久久久国产一级毛片| 久久久a久久爽久久v久久| 日韩视频在线欧美| 国产精品国产av在线观看| 亚洲无线观看免费| 女人久久www免费人成看片| 最近中文字幕2019免费版| 大话2 男鬼变身卡| 亚洲精品视频女| 99久久中文字幕三级久久日本| 久久影院123| 99久久精品国产国产毛片| 久久精品国产亚洲av天美| 大香蕉久久网| 日本wwww免费看| 成人特级av手机在线观看| 亚洲精品成人av观看孕妇| 少妇的逼水好多| 91午夜精品亚洲一区二区三区| 大片电影免费在线观看免费| 麻豆乱淫一区二区| 欧美变态另类bdsm刘玥| 亚洲av国产av综合av卡| 日日摸夜夜添夜夜爱| 国产精品伦人一区二区| 亚洲经典国产精华液单| 黑人高潮一二区| 日本欧美国产在线视频| 成人欧美大片| 日韩一本色道免费dvd| 国产一区二区亚洲精品在线观看| 国产69精品久久久久777片| 人妻一区二区av| 黄片无遮挡物在线观看| 嫩草影院入口| 国产日韩欧美在线精品| 久久99蜜桃精品久久| 久久综合国产亚洲精品| 亚洲国产精品国产精品| 久久久久久久久久人人人人人人| 夜夜看夜夜爽夜夜摸| av网站免费在线观看视频| 少妇的逼好多水| 国产黄色视频一区二区在线观看| 欧美人与善性xxx| 少妇被粗大猛烈的视频| 一个人观看的视频www高清免费观看| 欧美极品一区二区三区四区| 亚洲国产高清在线一区二区三| 亚州av有码| 天天躁日日操中文字幕| 乱系列少妇在线播放| 国产欧美日韩一区二区三区在线 | 精品一区二区三卡| 欧美激情国产日韩精品一区| 国产成人精品福利久久| 天堂中文最新版在线下载 | 欧美少妇被猛烈插入视频| 亚洲最大成人av| 高清欧美精品videossex| 啦啦啦啦在线视频资源| 欧美变态另类bdsm刘玥| 欧美三级亚洲精品| 国产精品爽爽va在线观看网站| 国产精品国产三级国产专区5o| 一个人看视频在线观看www免费| 美女主播在线视频| 亚洲,一卡二卡三卡| 亚洲人成网站在线播| 精品国产露脸久久av麻豆| 久久人人爽人人爽人人片va| 热re99久久精品国产66热6| 国产精品一区二区三区四区免费观看| 成人国产av品久久久| 青春草视频在线免费观看| 大话2 男鬼变身卡| 久久久精品94久久精品| 美女视频免费永久观看网站| 在线天堂最新版资源| 亚洲av男天堂| 国产视频内射| 在线a可以看的网站| 日韩三级伦理在线观看| 又爽又黄无遮挡网站| 一个人看的www免费观看视频| 久久99热这里只有精品18| 禁无遮挡网站| 国产伦在线观看视频一区| 搡女人真爽免费视频火全软件| 能在线免费看毛片的网站| 欧美一级a爱片免费观看看| 国产乱人视频| 在线观看免费高清a一片| 乱码一卡2卡4卡精品| 在线天堂最新版资源| xxx大片免费视频| 69人妻影院| 男人爽女人下面视频在线观看| 久久久久久久国产电影| 高清视频免费观看一区二区| 午夜日本视频在线| 一级a做视频免费观看| 天天躁日日操中文字幕| 国产69精品久久久久777片| 国产色婷婷99| 亚洲av日韩在线播放| 精品国产乱码久久久久久小说| 男女国产视频网站| 狂野欧美激情性bbbbbb| 中文字幕久久专区| 少妇高潮的动态图| 欧美日韩精品成人综合77777| 国产黄a三级三级三级人| 国产成人a∨麻豆精品| 久久99热6这里只有精品| 欧美一级a爱片免费观看看| 欧美最新免费一区二区三区| 七月丁香在线播放| 能在线免费看毛片的网站| 18禁动态无遮挡网站| 国产成人午夜福利电影在线观看| 久久精品久久久久久噜噜老黄| 久久国内精品自在自线图片| 日本熟妇午夜| 亚洲国产欧美人成| 观看免费一级毛片| 日本午夜av视频| 毛片女人毛片| 亚洲无线观看免费| 一本色道久久久久久精品综合| 青春草国产在线视频| 波野结衣二区三区在线| 成人漫画全彩无遮挡| 精品人妻一区二区三区麻豆| 久久久午夜欧美精品| 大片免费播放器 马上看| 精品一区二区三卡| 国产精品无大码| 大香蕉97超碰在线| 99re6热这里在线精品视频| 97超视频在线观看视频| 国产淫片久久久久久久久| 国产高清三级在线| 亚洲第一区二区三区不卡| 一级毛片久久久久久久久女| 新久久久久国产一级毛片| 国产精品国产三级专区第一集| 大片免费播放器 马上看| 久久久欧美国产精品| 日韩不卡一区二区三区视频在线| 最近的中文字幕免费完整| 成人亚洲欧美一区二区av| 久久久精品94久久精品| videos熟女内射| 亚洲精品日韩在线中文字幕| 国产亚洲精品久久久com| 不卡视频在线观看欧美| 激情五月婷婷亚洲| 国产一区有黄有色的免费视频| 只有这里有精品99| 国产淫片久久久久久久久| 成年版毛片免费区| 久久久久久久精品精品| 国产午夜精品一二区理论片| 久久久成人免费电影| 最近2019中文字幕mv第一页| 高清午夜精品一区二区三区| 亚洲aⅴ乱码一区二区在线播放| 国产淫语在线视频| 日日撸夜夜添| 欧美成人午夜免费资源| 国产精品无大码| 国产精品久久久久久精品电影小说 | 三级男女做爰猛烈吃奶摸视频| 一级毛片电影观看| 久久久久久久亚洲中文字幕| 精品国产三级普通话版| 欧美 日韩 精品 国产| 麻豆久久精品国产亚洲av| 国产成人a∨麻豆精品| 97超碰精品成人国产| av免费在线看不卡| 亚洲人成网站在线播| 日日啪夜夜撸| 亚洲国产色片| 全区人妻精品视频| 久久韩国三级中文字幕| 国产精品99久久久久久久久| a级毛片免费高清观看在线播放| 国产乱人偷精品视频| 欧美亚洲 丝袜 人妻 在线| 日韩免费高清中文字幕av| 在线精品无人区一区二区三 | 春色校园在线视频观看| 久久精品国产亚洲av涩爱| 一级片'在线观看视频| 国产91av在线免费观看| 亚洲成人中文字幕在线播放| 啦啦啦啦在线视频资源| 国内少妇人妻偷人精品xxx网站| 六月丁香七月| www.av在线官网国产| 国产精品爽爽va在线观看网站| 男女那种视频在线观看| 视频区图区小说| 国产69精品久久久久777片| 成人毛片a级毛片在线播放| av国产精品久久久久影院| 久热这里只有精品99| 亚洲av.av天堂| 美女视频免费永久观看网站| 国产午夜精品久久久久久一区二区三区| 国产片特级美女逼逼视频| 一个人看的www免费观看视频| 18禁在线播放成人免费| 91精品一卡2卡3卡4卡| xxx大片免费视频| 久久精品国产鲁丝片午夜精品| 亚洲天堂av无毛| 精品人妻熟女av久视频| av.在线天堂| 69av精品久久久久久| 国产毛片在线视频| 日韩强制内射视频| 波多野结衣巨乳人妻| 777米奇影视久久| av黄色大香蕉| 亚洲国产av新网站| 国产91av在线免费观看| 99热国产这里只有精品6| 青春草国产在线视频| 国产爱豆传媒在线观看| 久久国内精品自在自线图片| 免费观看在线日韩| 插阴视频在线观看视频| 熟女电影av网| 精品久久久精品久久久| 插逼视频在线观看| av国产久精品久网站免费入址| 日韩国内少妇激情av| 青春草亚洲视频在线观看| 久久这里有精品视频免费| 国产一区亚洲一区在线观看| 观看免费一级毛片| 各种免费的搞黄视频| 国产爽快片一区二区三区| 亚洲自拍偷在线| 麻豆乱淫一区二区| 亚洲精品,欧美精品| 狂野欧美白嫩少妇大欣赏| 亚洲第一区二区三区不卡| 97热精品久久久久久| 国产精品.久久久| 免费大片18禁| 日韩国内少妇激情av| 国产精品女同一区二区软件| 日韩成人伦理影院| 舔av片在线| 欧美潮喷喷水| 日韩av免费高清视频| 亚洲av成人精品一区久久| 久久99热这里只有精品18| 熟妇人妻不卡中文字幕| 日韩制服骚丝袜av| 亚洲图色成人| 高清日韩中文字幕在线| 国产一区有黄有色的免费视频| 久久久久久伊人网av| 直男gayav资源| 3wmmmm亚洲av在线观看| 免费看av在线观看网站| 亚洲精品成人久久久久久| 免费看av在线观看网站| 亚洲精品成人久久久久久| 男人狂女人下面高潮的视频| 婷婷色综合大香蕉| 中文字幕亚洲精品专区| 精华霜和精华液先用哪个| 国产精品久久久久久精品古装| 日本与韩国留学比较| 99热这里只有是精品在线观看| 国内少妇人妻偷人精品xxx网站| av女优亚洲男人天堂| 1000部很黄的大片| 国产美女午夜福利| 精品人妻偷拍中文字幕| 狂野欧美白嫩少妇大欣赏| 国产乱人视频| 国产视频内射| 免费观看a级毛片全部| 婷婷色av中文字幕| 哪个播放器可以免费观看大片| 男人狂女人下面高潮的视频| 日韩欧美精品v在线| 婷婷色av中文字幕| 少妇丰满av| 久久久久久久大尺度免费视频| 国产极品天堂在线| 成人二区视频| eeuss影院久久| 亚洲精品国产av蜜桃| 精华霜和精华液先用哪个| 欧美成人精品欧美一级黄| 深夜a级毛片| 性色av一级| 日产精品乱码卡一卡2卡三| 三级国产精品片| 久久99蜜桃精品久久| 干丝袜人妻中文字幕| 国产精品福利在线免费观看| 亚洲av不卡在线观看| 日韩精品有码人妻一区| 涩涩av久久男人的天堂| 97超视频在线观看视频| 美女被艹到高潮喷水动态| 2018国产大陆天天弄谢| a级一级毛片免费在线观看| 国产黄a三级三级三级人| 久热这里只有精品99| 丰满乱子伦码专区| 亚洲,欧美,日韩| 青青草视频在线视频观看| 国产伦在线观看视频一区| 日本av手机在线免费观看| 成人高潮视频无遮挡免费网站| 久久精品久久精品一区二区三区| 成年版毛片免费区| 春色校园在线视频观看| 国产永久视频网站| 久久久久性生活片| 婷婷色综合大香蕉| 又爽又黄a免费视频| 黑人高潮一二区| 国产淫语在线视频| 久久久精品欧美日韩精品| 亚洲,欧美,日韩| 国产av国产精品国产| 亚洲av二区三区四区| 欧美xxxx黑人xx丫x性爽| 一级毛片黄色毛片免费观看视频| 下体分泌物呈黄色| 国产黄频视频在线观看| 亚洲久久久久久中文字幕| 久久久成人免费电影| 日本一本二区三区精品| 有码 亚洲区| 日韩在线高清观看一区二区三区| av在线播放精品| 成人免费观看视频高清| 午夜老司机福利剧场| av.在线天堂| 下体分泌物呈黄色| 国产午夜精品久久久久久一区二区三区| 欧美成人精品欧美一级黄| 一区二区av电影网| 真实男女啪啪啪动态图| 高清av免费在线| 亚洲精华国产精华液的使用体验| 久久97久久精品| 久久久久久久久久久免费av| 国产精品熟女久久久久浪| 永久免费av网站大全| 最近2019中文字幕mv第一页| 免费观看a级毛片全部| 国产久久久一区二区三区| 久久久久久久久大av| 99久久精品国产国产毛片| 国产免费一级a男人的天堂| 水蜜桃什么品种好| 国产 一区精品| 国产91av在线免费观看| 五月玫瑰六月丁香| 国产精品不卡视频一区二区| av在线播放精品| 精品国产一区二区三区久久久樱花 | 一二三四中文在线观看免费高清| 欧美日韩综合久久久久久| 中文乱码字字幕精品一区二区三区| 国产黄色免费在线视频| 亚洲国产日韩一区二区| 欧美一区二区亚洲| www.av在线官网国产| 插阴视频在线观看视频| 亚洲精品自拍成人| 国产一级毛片在线| 精品国产三级普通话版| 亚洲三级黄色毛片| 综合色丁香网| 熟女电影av网| 秋霞在线观看毛片| 日韩不卡一区二区三区视频在线| 欧美一级a爱片免费观看看| 国产高清国产精品国产三级 | 国产精品秋霞免费鲁丝片| 老女人水多毛片| 国国产精品蜜臀av免费| 人妻制服诱惑在线中文字幕| 一区二区三区乱码不卡18| 成人毛片a级毛片在线播放| 啦啦啦啦在线视频资源| 99热网站在线观看| 小蜜桃在线观看免费完整版高清| 国产成人免费无遮挡视频| 午夜福利在线观看免费完整高清在| 丝袜脚勾引网站| av播播在线观看一区| 久久久久久久久久久丰满| 国产黄a三级三级三级人| 国产精品99久久久久久久久| 亚洲综合精品二区| 亚洲精品亚洲一区二区| 欧美高清性xxxxhd video| 黑人高潮一二区| 91精品一卡2卡3卡4卡| 一个人观看的视频www高清免费观看| 永久网站在线| 免费看av在线观看网站| 色吧在线观看| 久久亚洲国产成人精品v| 六月丁香七月| 日韩av不卡免费在线播放| 中文字幕亚洲精品专区| 午夜激情久久久久久久| 麻豆成人av视频| 一区二区三区乱码不卡18| 91午夜精品亚洲一区二区三区| 欧美日韩亚洲高清精品| 一本色道久久久久久精品综合| 免费看不卡的av| 欧美激情在线99| 成年女人看的毛片在线观看| 啦啦啦啦在线视频资源| 免费不卡的大黄色大毛片视频在线观看| 亚洲av中文字字幕乱码综合| 一区二区三区四区激情视频| 亚洲第一区二区三区不卡| 国产亚洲一区二区精品| 最近最新中文字幕免费大全7| 成人午夜精彩视频在线观看| 国精品久久久久久国模美| 一级毛片黄色毛片免费观看视频| 久久99热6这里只有精品| 99热网站在线观看| kizo精华| 精品久久久精品久久久| 日产精品乱码卡一卡2卡三| 亚洲国产精品国产精品| 久久ye,这里只有精品| .国产精品久久| 久久久久国产精品人妻一区二区| 99热国产这里只有精品6| 久久精品熟女亚洲av麻豆精品| 日韩成人av中文字幕在线观看| 亚洲电影在线观看av| 久久精品国产亚洲网站| 久久精品国产自在天天线| 日韩电影二区| 亚洲国产精品成人综合色| 三级国产精品欧美在线观看| 国产精品蜜桃在线观看| 亚洲国产欧美在线一区| 欧美人与善性xxx| 99久国产av精品国产电影| 深夜a级毛片| 天堂网av新在线| 69人妻影院| 亚洲精品aⅴ在线观看| 美女视频免费永久观看网站| 午夜激情久久久久久久| 精品酒店卫生间| 国产美女午夜福利| 菩萨蛮人人尽说江南好唐韦庄| 久久久欧美国产精品| 亚洲国产最新在线播放| 国产精品成人在线| 观看免费一级毛片| 综合色丁香网| 永久免费av网站大全| 亚洲人成网站在线播| 97在线视频观看| 三级男女做爰猛烈吃奶摸视频| 日韩一区二区三区影片| 久久久久久久久大av| 国产伦在线观看视频一区| 亚洲av免费高清在线观看| 3wmmmm亚洲av在线观看| 午夜视频国产福利| 午夜老司机福利剧场| av播播在线观看一区| 成人美女网站在线观看视频| 久久久久久久精品精品| 男的添女的下面高潮视频| 丝瓜视频免费看黄片| 久久久精品94久久精品| 99精国产麻豆久久婷婷| 免费看av在线观看网站| 九色成人免费人妻av| 国产精品一区二区三区四区免费观看| 亚洲欧美一区二区三区国产| 日本wwww免费看| 欧美日本视频| 美女cb高潮喷水在线观看| 91aial.com中文字幕在线观看| 日韩视频在线欧美| av卡一久久| 亚洲精品,欧美精品| 午夜精品一区二区三区免费看| 一二三四中文在线观看免费高清| 男人舔奶头视频| 国产色爽女视频免费观看| av在线播放精品| 亚洲精品亚洲一区二区| 丝袜喷水一区| 亚洲色图综合在线观看| 亚洲精品日韩在线中文字幕| 又黄又爽又刺激的免费视频.| 国精品久久久久久国模美| 亚洲一区二区三区欧美精品 | av在线天堂中文字幕| 国内精品美女久久久久久| 久久久久久久大尺度免费视频| 欧美少妇被猛烈插入视频| 插逼视频在线观看| 晚上一个人看的免费电影| 精品久久国产蜜桃| 人体艺术视频欧美日本| 干丝袜人妻中文字幕| 一级a做视频免费观看| 99视频精品全部免费 在线| 国产v大片淫在线免费观看| 日本猛色少妇xxxxx猛交久久| h日本视频在线播放| 成人鲁丝片一二三区免费| 午夜激情久久久久久久| 夫妻性生交免费视频一级片| 亚洲精品中文字幕在线视频 | 亚洲真实伦在线观看| 男人添女人高潮全过程视频| videossex国产| 亚洲精品成人久久久久久| 亚洲精华国产精华液的使用体验| 国产精品嫩草影院av在线观看|