Weather and Applied Climate

Exploring the interaction between the heat island effect and pollution island effect in Xi’an, China

Expand
  • 1. College of Urban and Environmental Sciences, Northwest University, Xi’an 710127, Shaanxi, China
    2. Shaanxi Provincial Key Laboratory of Surface System and Environmental Carrying Capacity, Xi’an 710127, Shaanxi, China
    3. Xi’an Urban Ecosystem Positioning Observation and Research Station, Xi’an 710127, Shaanxi, China

Received date: 2022-04-08

  Revised date: 2022-05-11

  Online published: 2023-01-17

Abstract

Surface/Canopy Urban Heat Island (SUHI/CUHI) effect and Atmospheric/Near-surface Urban Pollution Island (AUPI/NSUPI) effect interact and influence each other, significantly threatening the urban ecological environment. Based on the spatial coupling analysis and attribution method, the impact of AUPI on SUHI under radiation effect and CUHI on NSUPI under turbulence mixing in Xi’an city from 2003 to 2020 were explored using land surface temperature, air temperature, Aerosol Optical Depth (AOD), and PM2.5 data. The results indicated that: (1) Due to the difference in aerosol radiation effect between day and night in winter, SUHI intensity in winter is <0.2 K. The strong aerosol radiation cooling effect causes low ground temperature in urban areas and cooler in urban areas than in rural areas. When the SUHI intensity is greater than 2.2 K at night, the long-wave radiation effect of aerosol is enhanced, and the pollutant particles suspended in the urban space become the “insulation layer” of the city. (2) Significant CUHI in spring and summer enhanced atmosphere turbulent mixing, causing the diffusion of pollutant particles near the surface in urban regions. PM2.5 concentration and NSUPI intensity decreased correspondingly on urban surfaces. In autumn and winter, the atmospheric inversion layer obstructed air ascending movement driven by the CUHI effect. PM2.5 particles aggregated and accumulated in near-surface urban areas, and NSUPI was enhanced accordingly. Additionally, the contribution of haze to surface heat island by attribution quantitative analysis suggested that AOD in rural or urban areas was significantly negatively correlated with SUHI at night and correlation coefficients were -0.431 and -0.386, respectively. This suggested that the main radiation effect of haze on the surface heat environment at night was the cooling effect, while the weakening or strengthening effect of haze on the local climate of urban heat islands was mainly attributed to the positive or negative difference in AOD in urban and rural areas. The UHI and UPI effects are inseparable. It is very important to promote the comprehensive study of urban climate and pollution for constructing a green urban ecological environment.

Cite this article

JIANG Ziqi,WANG Xuhong,FENG Zihao,CUI Siying,YANG Xia . Exploring the interaction between the heat island effect and pollution island effect in Xi’an, China[J]. Arid Zone Research, 2022 , 39(6) : 1768 -1781 . DOI: 10.13866/j.azr.2022.06.07

References

[1] Oke T R. The energetic basis of the urban heat island[J]. Quarterly Journal of the Royal Meteorological Society, 1982, 108(455): 1-24.
[2] Zhao S Q, Zhou D C, Liu S G. Data concurrency is required for estimating urban heat island intensity[J]. Environmental Pollution, 2016, 208(Pt A): 118-124.
[3] Chakraborty T, Lee X. A simplified urban-extent algorithm to characterize surface urban heat islands on a global scale and examine vegetation control on their spatiotemporal variability[J]. International Journal of Applied Earth Observation and Geoinformation, 2019, 74: 269-280.
[4] Deilami K, Kamruzzaman M, Liu Y. Urban heat island effect: A systematic review of spatio-temporal factors, data, methods, and mitigation measures[J]. International Journal of Applied Earth Observation and Geoinformation, 2018, 67: 30-42.
[5] Crutzen P J. New Directions: The growing urban heat and pollution“island”effect-impact on chemistry and climate[J]. Atmospheric Environment, 2004, 38(21): 3539-3540.
[6] Ulpiani G. On the linkage between urban heat island and urban pollution island: Three-decade literature review towards a conceptual framework[J]. Science of the Total Environment, 2020, 751(38): 141727, doi: 10.1016/j.scitotenv.2020.141727.
[7] Ohara T, Akimoto H, Kurokawa J-I, et al. An Asian emission inventory of anthropogenic emission sources for the period 1980-2020[J]. Atmospheric Chemistry and Physics, 2007, 7(16): 4419-4444.
[8] Bonn B, Von Schneidemesser E, Andrich D, et al. BAERLIN2014-the influence of land surface types on and the horizontal heterogeneity of air pollutant levels in Berlin[J]. Atmospheric Chemistry and Physics, 2016, 16(12): 7785-7811.
[9] Pongpiachan S, Ho K F, Cao J J. Estimation of gas-particle partitioning coefficients (Kp) of carcinogenic polycyclic aromatic hydrocarbons in carbonaceous aerosols collected at Chiang-Mai, Bangkok and Hat-Yai, Thailand[J]. Asian Pacific Journal of Cancer Prevention, 2013, 14(4): 2461-2476.
[10] He B-J. Potentials of meteorological characteristics and synoptic conditions to mitigate urban heat island effects[J]. Urban Climate, 2018, 24: 26-33.
[11] Jin M S, Kessomkiat W, Pereira G. Satellite-observed urbanization characters in Shanghai, China: aerosols, urban heat island effect, and land-atmosphere interactions[J]. Remote Sensing, 2011, 3(1): 83-99.
[12] Jacobson M Z. Studying the effects of aerosols on vertical photolysis rate coefficient and temperature profiles over an urban airshed[J]. Journal of Geophysical Research, 1998, 103(D9): 10593-10604.
[13] Li H D, Meier F, Lee X H, et al. Interaction between urban heat island and urban pollution island during summer in Berlin[J]. Science of the Total Environment, 2018, 636: 818-828.
[14] 梁秀娟, 王旭红, 牛林芝, 等. 大西安都市圈城市热岛效应时空分布特征及AOD对热岛强度的影响研究[J]. 生态环境学报, 2020, 29(8): 1566-1580.
[14] [ Liang Xiujuan, Wang Xuhong, Niu Lingzhi, et al. Research on the temporal and spatial distribution characteristics of urban heat island effect and the influence of AOD on urban heat island intensity in the greater Xi’an metropolitan area[J]. Ecology and Environmental Sciences, 2020, 29(8): 1566-1580. ]
[15] 曹畅, 李旭辉, 张弥, 等. 中国城市热岛时空特征及其影响因子的分析[J]. 环境科学, 2017, 38(10): 3987-3997.
[15] [ Cao Chang, Li Xuhui, Zhang Mi, et al. Correlation analysis of the urban heat island effect and its impact factors in China[J]. Environmental Science, 2017, 38(10): 3987-3997. ]
[16] Sarrat C, Lemonsu A, Masson V, et al. Impact of urban heat island on regional atmospheric pollution[J]. Atmospheric Environment, 2006, 40(10): 1743-1758.
[17] Fallmann J, Forkel R, Emeis S. Secondary effects of urban heat island mitigation measures on air quality[J]. Atmospheric Environment, 2016, 125(t A): 199-211.
[18] Zhong J T, Zhang X Y, Wang Y Q, et al. The two-way feedback mechanism between unfavorable meteorological conditions and cumulative aerosol pollution in various haze regions of China[J]. Atmospheric Chemistry and Physics, 2019, 19(5): 3287-3306.
[19] Ngarambe J, Joen S J, Han C-H, et al. Exploring the relationship between particulate matter, CO, SO2, NO2, O3 and urban heat island in Seoul, Korea[J]. Journal of Hazardous Materials, 2021, 403: 123615, doi: 10.1016/j.jhazmat.2020.123615.
[20] 胡琳, 程路, 林扬, 等. 关中区域大气重污染年份气象条件分析[J]. 干旱区研究, 2020, 37(6): 1496-1503.
[20] [ Hu Lin, Cheng Lu, Lin Yang, et al. A conceptual model of regional pollution and meteorological conditions in Guanzhong region[J]. Arid Zone Research, 2020, 37(6): 1496-1503. ]
[21] Yao R, Wang L C, Huang X, et al. Temporal trends of surface urban heat islands and associated determinants in major Chinese cities[J]. Science of the Total Environment, 2017, 609: 742-754.
[22] Han G F, Xu J H. Land surface phenology and land surface temperature changes along an urban-rural gradient in Yangtze River Delta, China[J]. Environmental Management, 2013, 52(1): 234-249.
[23] Wei J, Li Z Q, Lyapustin A, et al. Reconstructing 1 km-resolution high-quality PM2.5 data records from 2000 to 2018 in China: spatiotemporal variations and policy implications[J]. Remote Sensing of Environment, 2021, 252: 112136, doi: 10.1016/j.rse.2020.112136.
[24] Zhong C, Chen C, Liu Y, et al. A specific study on the impacts of PM2.5 on urban heat islands with detailed in situ data and satellite images[J]. Sustainability, 2019, 11(24): 7075, doi: 10.3390/su112 47075.
[25] 刘巧婧, 王莉红. 城市化与生态环境耦合协调关系研究——以杭州市为例[J]. 环境科学学报, 2018, 38(10): 4214-4222.
[25] [ Liu Qiaojing, Wang Lihong. Examination of a coupling coordination relationship between urbanization and the eco-environment: Case study of Hangzhou[J]. Acta Scientiae Circumstantiae, 2018, 38(10): 4214-4222. ]
[26] Li X, Goulden M L, Hollinger D Y, et al. Observed increase in local cooling effect of deforestation at higher latitudes[J]. Nature, 2011, 479(7373): 384-387.
[27] Zhao L, Li X H, Smith R B, et al. Strong contributions of local background climate to urban heat islands[J]. Nature, 2014, 511(7508): 216-219.
[28] Cao C, Li X H, Liu S D, et al. Urban heat islands in China enhanced by haze pollution[J]. Nature Communications, 2016, 7(1): 12509, doi: 10.1038/ncomms12509.
[29] Lu L L, Weng Q H, Xiao D, et al. Spatiotemporal variation of surface urban heat islands in relation to land cover composition and configuration: A multi-scale case study of Xi’an, China[J]. Remote Sensing, 2020, 12(17): 2713, doi: 10.3390/rs12172713.
[30] Voogt J A, Oke T R. Thermal remote sensing of urban climates[J]. Remote Sensing of Environment, 2003, 86(3): 370-384.
[31] Sun H, Chen Y H, Zhan W F. Comparing surface-and canopy-layer urban heat islands over Beijing using MODIS data[J]. International Journal of Remote Sensing, 2015, 36(21): 5448-5465.
[32] 王钊, 彭艳, 车慧正, 等. 近10年关中盆地MODIS气溶胶的时空变化特征[J]. 高原气象, 2013, 32(1): 234-242.
[32] [ Wang Zhao, Peng Yan, Cheng Huizheng, et al. Analyses on spatial and temporal characteristics of AOD in Guanzhong region of Shaanxi Province using long term MODIS data[J]. Plateau Meteorology, 2013, 32(1): 234-242. ]
[33] 郑玉蓉, 王旭红, 崔思颖, 等. 基于地基太阳光度计观测的长安区气溶胶光学特性变化及其与颗粒物浓度的关系[J]. 环境科学, 2022, 43(7): 3494-3507.
[33] [ Zheng Yurong, Wang Xuhong, Cui Siying, et al. Aerosol optical characteristics with ground-based measurements by sun photometer and its relationship with PM particle concentration in Chang’an[J]. Environmental Science, 2022, 43(7): 3494-3507. ]
[34] 刘随心, 曹军骥, 安芷生. 西安大气细粒子(PM2.5)质量浓度变化特征及其影响因素[J]. 过程工程学报, 2009, 9(S2): 231-236.
[34] [ Liu Suixin, Cao Junji, An Zhisheng. Characterization of ambient fine particles (PM2.5) concentration and its influential factors in Xi’an[J]. The Chinese Journal of Process Engineering, 2009, 9(S2): 231-236. ]
[35] Wei N, Wang N L, Huang X, et al. The effects of terrain and atmospheric dynamics on cold season heavy haze in the Guanzhong Basin of China[J]. Atmospheric Pollution Research, 2020, 11(10): 1805-1819.
[36] Wang L L, Gao Z Q, Miao S G, et al. Contrasting characteristics of the surface energy balance between the urban and rural areas of Beijing[J]. Advances in Atmospheric Sciences, 2015, 32(4): 505-514.
[37] Wu H, Wang T J, Riemer N, et al. Urban heat island impacted by fine particles in Nanjing, China[J]. Scientific Reports, 2017, 7(1): 11422, doi: 10.1038/s41598-017-11705-z.
[38] 王琮淙, 邱国玉, 黄晓峰. 城市热岛效应与PM2.5的关系研究[J]. 干旱区资源与环境, 2018, 32(5): 191-195.
[38] [ Wang Congcong, Qiu Guoyu, Huang Xiaofeng. Relationship between urban heat island and PM2.5[J]. Journal of Arid Land Resources and Environment, 2018, 32(5): 191-195. ]
[39] 刘子龙, 代斌, 崔卓彦, 等. 大气污染物浓度变化特征及潜在源分析——以乌鲁木齐为例[J]. 干旱区研究, 2021, 38(2): 562-569.
[39] [ Liu Zilong, Dai Bin, Cui Zhuoyan, et al. Concentration characteristics and potential source of atmospheric pollutants: A case study in Urumqi[J]. Arid Zone Research, 2021, 38(2): 562-569. ]
[40] Yang Y J, Zheng Z F, Yim S Y L, et al. PM2.5 pollution modulates wintertime urban heat island intensity in the Beijing-Tianjin-Hebei megalopolis, China[J]. Geophysical Research Letters, 2020, 47(1), doi: 10.1029/2019GL084288.
[41] Wu H, Wang T J, Wang Q G, et al. Radiative effects and chemical compositions of fine particles modulating urban heat island in Nanjing, China[J]. Atmospheric Environment, 2021, 247: 118201, doi: 10.1016/j.atmosenv.2021.118201.
[42] 余光明, 徐建中, 康世昌, 等. 祁连山老虎沟地区大气颗粒物输送轨迹及潜在源区[J]. 干旱区研究, 2020, 37(3): 671-679.
[42] [ Yu Guangming, Xu Jianzhong, Kang Shichang, et al. Trajectory analysis of atmospheric transport of particles in Laohugou area,western Qilian Mountains[J]. Arid Zone Research, 2020, 37(3): 671-679. ]
[43] 张强, 吕世华, 张广庶. 山谷城市大气边界层结构及输送能力[J]. 高原气象, 2003, 22(4): 346-353.
[43] [ Zhang Qiang, Lv Shihua, Zhang Guangshu. The structure of atmospheric boundary layer over valley city and its transfer ability[J]. Plateau Meteorology, 2003, 22(4): 346-353. ]
[44] 张强. 地形和逆温层对兰州市污染物输送的影响[J]. 中国环境科学, 2001, 21(3): 230-234.
[44] [ Zhang Qiang. The influence of terrain and inversion layer on pollutant transfer over Lanzhou City[J]. China Environmental Science, 2001, 21(3): 230-234. ]
[45] 张强. 兰州大气污染物浓度与局地气候环境因子的关系[J]. 兰州大学学报, 2003, 39(1): 99-106.
[45] [ Zhang Qiang. A study of the interaction between concentration of pollutants and the climatic and environmental factors of Lanzhou[J]. Journal of Lanzhou University, 2003, 39(1): 99-106. ]
[46] Zhang Q, Li H Y. A study of the relationship between air pollutants and inversion in the ABL over the city of Lanzhou[J]. Advances in Atmospheric Sciences, 2011, 28(4): 879-886.
[47] 胡隐樵, 张强. 兰州山谷大气污染的物理机制与防治对策[J]. 中国环境科学, 1999, 19(2): 119-122.
[47] [ Hu Yinqiao, Zhang Qiang. Atmosphere pollution mechanism along with prevention and cure countermeasure of the Lanzhou hollow basin[J]. China Environmental Science, 1999, 19(2): 119-122. ]
Outlines

/