Spatiotemporal variations of AOD and geographical detection of its influence factors in Beijing-Tianjin-Hebei region

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  • 1College of Geography and Environment Science,Tianjin Normal University,Tianjin 300387,China; 2 Xian Institute for Innovative Earth Environmental Research,Xian 710061,Shaanxi,China

Received date: 2019-05-01

  Revised date: 2019-08-27

  Online published: 2020-01-05

Abstract

The Beijing-Tianjin-Hebei region, which is located in the Bohai Rim, is the most economically developed region in northern China. It is also one of the most polluted regions in China. Aerosol optical depth (AOD) can effectively reflect the degree of air pollution. In this study, the MODIS 3 km AOD remote sensing data was analyzed and the research results would be of great significance to China’s air pollution. Firstly, the temporal variation characteristics and spatial autocorrelation characteristics of AOD in Beijing-Tianjin-Hebei region from 2010 to 2016 were analyzed. The factors of precipitation, wind speed, relative humidity, normalized difference vegetation index (NDVI),gross domestic product (GDP),secondary industry GDP, population density were selected as the affecting factors of AOD, using geographical detection to analyze the trend of the factors contribution ratio and its dominant affecting factors in different regions and different times in Beijing-Tianjin-Hebei region. The results showed as follows: (1) The annual average AOD of the Beijing-Tianjin-Hebei region was 0.83 from 2010 to 2016.The annual average AOD of Tianjin was the highest in the study area, followed by Hebei and Beijing. The annual variation trend of AOD was shown an overall state of decline first followed by rise and then a small fluctuation change and a similar status in each local region as well. (2) The spatial autocorrelation analysis indicated a significant positive correlation among spatial distribution of AOD in Beijing-Tianjin-Hebei region. Local high-accumulation areas were mainly concentrated in the southeastern part of Beijing, southern part of Tianjin, and central-southern part of Hebei Province. The low-accumulation areas were concentrated in the mountains of the northwest. The area of the high and low accumulation areas in Beijing-Tianjin-Hebei region showed a decreasing trend, while the area of the non-significant areas showed an increasing trend. (3) Geographic detection analysis indicated that the primary influencing factor was NDVI in Beijing, followed by population density, and their interaction was significant. The dominant factor was wind speed in Tianjin. The effect of human factors such as population density and the GDP of the secondary industry were also important. The effect of interactions between wind speed and the above factors were also significant. The dominant factor was population density in Hebei Province, followed by GDP and the secondary industry’s GDP, and the overall interaction was relatively weak. In the past, the correlation analysis of the influencing factors was based on linear relationship of the overall area, while the geographical detection not only has wireless assumptions, but also reveals the linear, nonlinear and spatial relationships of the driving factors. From this perspective, the geographical detection is more reliable in studying the influencing factors. This study applied geographical detection to analysis of the impacting factors of AOD in Beijing-Tianjin-Hebei region, which proved its feasibility in this field and this region. At the same time, the results also had important reference value for air pollution prevention, industrial and agricultural layout and urban construction in Beijing-Tianjin-Hebei region.

Cite this article

JING Yue, SUN Yan-ling, GAO Shuang, CHEN Li, PAN Long, MA Han . Spatiotemporal variations of AOD and geographical detection of its influence factors in Beijing-Tianjin-Hebei region[J]. Arid Land Geography, 2020 , 43(1) : 87 -98 . DOI: 10.12118/j.issn.1000-6060.2020.01.11

References

[1]VINEIS P,HUSGAFVEL-PURSIAINEN K.Air pollution and cancer:Biomarker studies in human populations[J].Carcinogenesis,2005,26(11):1846-1855. [2]刘浩,高小明,谢志英,等.京津冀晋鲁区域气溶胶光学厚度的时空特征[J].环境科学学报,2015,35(5):1506-1511.[LIU Hao,GAO Xiaoming,XIE Ziying,et al.Spatio-temporal characteristics of aerosol optical depth over Beijing-Tianjin-Hebei-Shanxi-Shandong region during 2000—2013[J].Acta Scientiae Circumstantiae,2015,35(5):1506-1511.] [3]李成才,毛节泰,刘启汉,等.利用MODIS光学厚度遥感产品研究北京及周边地区的大气污染[J].大气科学,2003,27(5):869-880.[LI Chengcai,MAO Jietai,Alexis Kaihon LAU,et al.Research on the air pollution in Beijing and its surroundings with MODIS AOD products[J].Chinese Journal of Atmospheric Sciences,2003,27(5):869-880.] [4]CHU D A,KAUFMAN Y J,ICHOKU C,et al.Validation of MODIS aerosol optical depth retrieval over land[J].Geophysical Research Letters,2002,29(12):8007. [5]罗云峰,吕达仁,周秀骥,等.30年来我国大气气溶胶光学厚度平均分布特征分析[J].大气科学,2002,(6):721-730.[LUO Yunfeng,LYU Daren,ZHOU Xiuji,et al.Analyses on the spatial distribution of aerosol optical depth over China in recent 30 years[J].Chinese Journal of Atmospheric Sciences,2002,(6):721-730.] [6]关佳欣,李成才.我国中、东部主要地区气溶胶光学厚度的分布和变化[J].北京大学学报,2010,46(2):185-191.[GUAN Jiaxin,LI Chengcai.Spatial distributions and changes of aerosol optical depth over eastern and central China[J].Acta Scientiarum Naturalium Universitatis Pekinensis,2010,46(2):185-191.] [7]MUNCHAK L A,MATTOO S,LEVY R C,et al.The MODIS 3 km aerosol product:Applications over an urban/suburban landscape during DISCOVER-AQ[C].Agu Fall Meeting,2012,12. [8]张西雅,启海波.京津冀地区气溶胶时空分布及与城市化关系的研究[J].大气科学,2017,41 (4):797-810.[ZHANG Xiya,QI Haibo.Spatio-temporal characteristics of aerosol optical depth and their relationship with urbanization over Beijing-Tianjin-Hebei region[J].Chinese Journal of Atmospheric Sciences,2017,41(4):797-810.] [9]孙晓雷,甘伟,林燕,等.MODIS 3 km气溶胶光学厚度产品检验及其环境空气质量指示[J].环境科学学报,2015,35(6):1657-1666.[SUN Xiaolei,GAN Wen,LIN Yan,et al.Validation of MODIS 3 km aerosol optical depth product and its air quality indication[J].Acta Scientiae Circumstantiae,2015,35(6):1657-1666.] [10]景悦,孙艳玲,付宏臣,等.2010—2016年京津冀AOD时空变化及其影响因子分析[J].环境科学与技术,2018,41(8):104-113.[JING Yue,SUN Yanling,FU Hongchen,et al.Temporal and spatial variation of aerosol optical depth and analysis of influencing factors in Beijing-Tianjin-Hebei region from 2010 to 2016[J].Environmental Science & Technology,2018,41(8):104-113.] [11]刘状,孙曦亮,刘丹,等.2001—2017年中国北方省份气溶胶光学厚度的时空特征[J].环境科学学报,2018,38(8):3177-3184.[LIU zhuang,SUN Xiliang,LIU Dan,et al.Spatiotemporal characteristics of aerosol optical depth over Beijing-Tianjin-Hebei-Shandong-Henan-Shanxi-Shaanxi region during 2001—2017[J].Acta Scientiae Circumstantiae,2018,38(8):3177-3184.] [12]董自鹏,余兴,李星敏,等.基于MODIS数据的陕西省气溶胶光学厚度变化趋势与成因分析[J].科学通报,2014,59(3):306-316.[DONG Zipeng,YU Xing,LI Xingmin,et al.Analysis of aerosol optical thickness variation and its causes in Shaanxi Province based on MODIS data[J].Chinese Science Bulletin,2014,59(3):306-316.] [13]张宸赫,赵天良,王富,等.2003—2014年东北三省气溶胶光学厚度变化分析[J].环境科学,2017,38(2):476-484.[ZHANG Chenhe,ZHAO Tianliang,Wang Fu,et al.Variations in aerosol optical depth over three northeastern provinces of China in 2003—2014[J].Environmental Science,2017,38 (2):476-484.] [14]张静怡,卢晓宁,洪佳,等.2000—2014年四川省气溶胶时空格局及其驱动因子定量研究[J].自然资源学报,2016,31(9):1514-1525.[ZHANG Jingyi,LU Xiaoning,HONG Jia,et al.Quantitative study on temporal and spatial patterns of aerosol optical depth and its driving forces in Sichuan Province during 2000—2014[J].Journal of Natural Resources,2016,31(9):1514-1525.] [15]高宇潇,刘志辉,王敬哲.乌鲁木齐市PM-2.5浓度与MODIS气溶胶光学厚度相关性分析[J].干旱区地理,2018,41(2):298-305.[GAO Yuxiao,LIU Zhihui,WANG Jingzhe.Correlation analysis of PM-2.5 concentration and MODIS aerosol optical depth in Urumqi City[J].Arid Land Geography,2018,41(2):298-305.] [16]WANG J F,HU Y.Environmental health risk detection with GeogDetector[J].Environmental Modelling & Software,2005,20(10):114-115. [17]刘小鹏,王可,叶均艳,等.宁夏水贫困地域分异的WPI-Geodetector测度与分析[J].干旱区地理,2018,41(1):160-169.[LIU Xiaopeng,,WANG Ke,YE Junyan,et al.Measurement and analysis of spatial-temporal differentiation of water poverty in Ningxia based on WPI-geodetector[J].Arid Land Geography,2018,41(1):160-169.] [18]LOU C R,LIU H Y,LI Y F,et al.Socioeconomic drivers of PM-2.5 in the accumulation phase of air pollution episodes in the Yangtze River Delta of China[J].International Journal of Environmental Research & Public Health,2016,13(10):928. [19]马小雯,章笑艺,来丽芳,等.基于地理探测器的浙江省空气质量风险因子分析[J].浙江大学学报(理学版),2018,45(3):351-362.[MA Xiaowen,ZHANG Xiaoyi,LAI Lifang,et al.Study on risk factors of air quality in Zhejiang Province based on geographical detectors[J].Journal of Zhejiang University (Science Edition),2018,45(3):351-362.] [20]周亮,周成虎,杨帆,等.2000—2011年中国PM-2.5时空演化特征及驱动因素解析[J].地理学报,2017,72(11):2079-2092.[ZHOU Liang,ZHOU Chenghu,YANG Fan,et al.Spatio-temporal evolution and the influencing factors of PM-2.5 in China between 2000 and 2011[J].Acta Geographica Sinice,2017,72(11):2079-2092.] [21]郭春颖,施润和,周云云,等.基于遥感与地理探测器的长江三角洲空气污染风险因子分析[J].长江流域资源与环境,2017,26(11):1805-1814.[GUO Chunying,SHI Runhe,ZHOU Yunyun,et al.Analysis on risk factors of air pollution over the Yangze River Delta using remote sensing and geographical detector[J].Resources and Environment in the Yangtze Basin,2017,26(11):1805-1814.] [22]魏继德.空间插值方法的比较与优化[D].福州:福州大学,2010.[WEI Jide.The comparison and optimization of spatial interpolation approaches[D].Fuzhou:Fuzhou University,2010.] [23]王振波,方创琳,许光,等.2014年中国城市PM-2.5浓度的时空变化规律[J].地理学报,2015,70(11):1720-1734.[WANG Zhenbo,FANG Chuanglin,XU Guang,et al.Spatial-temporal characteristics of the PM-2.5 in China in 2014[J].Acta Geographica Sinice,2015,70(11):1720-1734.] [24]王劲峰,徐成东.地理探测器:原理与展望[J].地理学报,2017,72(1):116-134.[WANG Jinfeng,XU Chengdong.Geodetector:Principle and prospective[J].Acta Geographica Sinice,2017,72(1):116-134.] [25]HE Q,HUANG B.Satellite-based mapping of daily high-resolution ground PM-2.5 in China via space-time regression modeling[J].Remote Sensing of Environment,2018,206:72-83. [26]MA Z,HU X,SAYER AM,et al.Satellite-Based Spatiotemporal Trends in PM-2.5 Concentrations:China,2004—2013[J].Environ Health Perspect,2016,124(2):184-192. [27]LYU B,HU Y,CHANG H H,et al.Daily estimation of ground-level PM-2.5 concentrations at 4 km resolution over Beijing-Tianjin-Hebei by fusing MODIS AOD and ground observations[J].Science of the Total Environment,2017,580:235-244.
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