基于无人机观测的塔克拉玛干沙漠反应性气体特征及来源分析

Characterization of Reactive Gas and Source Analysis in Taklimakan Desert Based on Unmanned Aerial Vehicle Observation

  • 摘要: 为研究沙漠地区大气环境和反应性气体变化机理,利用无人机观测平台于春季(2022年5月8—30日)和夏季(2021年7月19—31日)对塔克拉玛干沙漠中心(塔中站)和南缘(民丰站)的反应性气体体积分数、气温、相对湿度和风速进行垂直观测,对比沙漠腹地和边缘的反应性气体垂直变化,结合HYSPLIT模式究其来源. 结果表明:①民丰站CO体积分数整体略高于塔中站,春季CO体积分数明显高于夏季,并且可能存在较强的SO2和NO2污染现象. CO平均体积分数呈民丰站春季(524.68×10−9)>民丰站夏季(468.95×10−9)>塔中站春季(313.42×10−9)>塔中站夏季(133.64×10−9)的特征;SO2体积分数夏季高于春季,呈民丰站夏季(105.22×10−9)>民丰站春季(69.21×10−9)>塔中站夏季(65.38×10−9)>塔中站春季(49.98×10−9)的特征;塔中站NO2体积分数整体高于民丰站,呈塔中站春季(158.95×10−9)>塔中站夏季(155.10×10−9)>民丰站春季(131.58×10−9)>民丰站夏季(127.23×10−9)的特征,并与O3体积分数显著相关;夏季O3体积分数明显高于春季,呈塔中站夏季(51.22×10−9)>民丰站夏季(24.23×10−9)>塔中站春季(11.90×10−9)>民丰站春季(11.67×10−9)的特征. ②塔中站和民丰站两地反应性气体垂直廓线变化特征显著,CO体积分数随着高度的升高而增加,且受风速变化影响;SO2体积分数多呈波动性变化特征;NO2体积分数白天高于夜间,垂直方向上的变化存在波动,近地面NO2出现累积;O3体积分数垂直廓线呈明显的昼夜特征. ③春季塔中站反应性气体大部分可能由“东灌”气流远距离输送而来;夏季塔中站反应性气体体积分数主要受盆地北缘绿洲带人为活动影响. 春季民丰站的反应性气体多来自盆地边缘的人为活动集中区,反应性气体体积分数较大,夏季气流均起源于沙漠内部,因此这可能是导致春夏季反应性气体体积分数差异的原因. 研究显示,春季、夏季塔中站和民丰站的反应性气体体积分数水平存在明显差异,人为活动较为集中的区域贡献了较高的反应性气体体积分数.

     

    Abstract: The vertical structures of reactive gas concentrations, air temperature, relative humidity and wind speed were observed in the center (Tazhong station) and southern edge (Minfeng station) of the Taklamakan Desert during 21st-31st July 2021 and 8th-29th May 2022 using an unmanned airplane observation platform to compare the vertical variations of reactive gases in the hinterland and southern edge, and the source was further investigated in combination with the HYSPLIT model. The results show that: (1) The overall CO concentration at Minfeng station is slightly higher than that at Tazhong station, the CO concentration in spring is significantly higher than that in summer, and there may be high concentrations of SO2 and NO2. The average CO concentration was as follows: Minfeng station spring (524.68×10−9 ) >Minfeng station summer (468.95×10−9) >Tazhong station spring (313.42×10−9) >Tazhong station summer (133.64×10−9). The SO2 concentration in summer was higher than that in spring with the characteristics of Minfeng station summer (105.22×10−9) >Minfeng station spring (69.21×10−9) >Tazhong station summer (65.38×10−9) >Tazhong station spring (49.98×10−9). The overall NO2 concentration at Tazhong station were higher than that at Minfeng station with spring at Tazhong station (158.95×10−9) >summer at Tazhong station (155.10×10−9) >spring at Minfeng station (131.58×10−9) >summer at Minfeng station (127.23×10−9), which correlated with the change of O3 concentration. The O3 concentration in summer was significantly higher than that in spring, showing the characteristics of summer at Tazhong station (51.22×10−9) >summer at Minfeng station (24.23×10−9) >spring at Tazhong station (11.90×10−9) >spring at Minfeng station (11.67×10−9). (2) The vertical profile of reactive gases at Tazhong station and Minfeng station changed significantly, and CO concentration increased with height and was affected by change of wind speed. SO2 concentration was mostly characterized by fluctuating changes. NO2 concentration was higher during the day than at night, and the concentration of NO2 near the ground was higher. O3 concentration showed obvious diurnal change in the vertical profile. (3) Most of the reactive gases in the spring are likely to be transported over long distances by the ‘Eastern Irrigation’ airflows. The reactive gas concentration at Tazhong station in summer was mainly affected by human activities in the oasis zone on the northern edge of the basin. The spring airflow at Minfeng station came from the county area on the southern edge of the basin, where human activities were relatively concentrated and contributed a larger concentration of reactive gases. The summer airflows at Minfeng station all originated from the interior of the desert, which may lead to differences in reactive gas concentrations in spring and summer. The study shows that there are significant differences in reactive gas concentrations at Tazhong station and Minfeng station in spring and summer, and the areas with high human activities contribute to high reactive gas concentrations.

     

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