شهرها و بازخورد های آب و هوایی آن(ابر-بارش) مطالعه موردی: کلان شهر تهران

نوع مقاله : مقاله کامل

نویسندگان

1 گروه جغرافیای طبیعی دانشگاه شهید بهشتی

2 دانشگاه شهید بهشتی

چکیده

در این مطالعه توسعه فیزیکی شهر تهران در سه دهه گذشته(2022-1992)، با کمک شاخص توسعه فیزیکی شهری بر روی تصاویر لندست اعمال گردید. متناسب با روند توسعه فیزیکی، ویژگیهای بارش ها، ارتفاع پایه ابر در تقابل با میدان آئروسل ها و کیفیت هوا با استفاده از کدهای سینوپ و داده های آلاینده شرکت کنترل کیفیت هوای تهران با بکارگیری بسته Corrplot در محیط برنامه نویسی R محاسبه گردید. در سه دهه گذشته تهران از روند رو به رشد سریعی(R=0.97) برخوردار بوده است و به همان نسبت مناطق طبیعی سطح کلانشهر (R=-0.98) در حال کاهش می باشند. متناسب با روند گسترش شهری، نسبت روزهای برفی با شدت بیش از اندازه ای(R=-0.94) کاهش یافته است. در اتمسفر شهر تهران بین مقادیر بارش همرفتی رخ داده و عمق اپتیکی آئروسل ها، همبستگی مثبت با مقدار آماری معنی داری مشاهده می شود. همچنین بین آلاینده های هوا و ارتفاع پایین ترین لایه ابر همبستگی منفی معنادار قابل توجهی وجود دارد، نتایج همبستگی نشان می دهد که ابرها با لایه مرزی شهری جفت شده و هوای آلوده شهری را در خود جذب و اندازه توزیع قطرات را تغییر می دهند که این امر منجر به کاهش ارتفاع پایه ابر نسبت به سطح زمین می شود.

کلیدواژه‌ها

موضوعات


عنوان مقاله [English]

Cities and their weather feedback (Cloud- Precipitation) Case Study: Tehran Metropolis

نویسندگان [English]

  • Ghasem Kikhosravei 1
  • Nazanin Hosseini Nia 2
1 Shahid Beheshti University
2 Shahid Beheshti University
چکیده [English]

Introduction:

Tehran is regarded as one of the most polluted cities in the world. This situation results from several factors, including the city's topography, its large population, incomplete combustion from vehicles, the irregular landscape of high-rise buildings without scientific standards, and the unconventional use of fossil fuels for heating and cooling homes. The factors mentioned above, along with the unprecedented expansion of urbanization over the past half century, have certainly affected the behavior of meteorological elements. Therefore, this study attempts to examine the effects of the city and its climatic feedbacks on clouds and precipitation characteristics, especially in the warm seasons when convective precipitation dominates, over a 30-year statistical period.

Methodology:

The time series data used in this study include hourly and daily data from meteorological stations and daily data from air quality monitoring stations, Landsat 7 and 8 ETM and OLI/TIR images, and the aerosol optical depth (AOD) product from the MODIS sensor for the period 1993 to 2022. Meteorological data of current weather codes (ww) related to convective precipitation (Sinop codes 80 to 90 for convective precipitation, codes 91 to 99 for storms, as well as codes where showers and thunderstorms occur outside the station include codes 17-19-25-27 and 29, which are in the convective precipitation group) and snowfall (Sinop codes 70 to 79), precipitation (R, mm), and the height of the lowest cloud layer (HL1) were received from the National Meteorological Organization (https://data.irimo.ir). Similarly, data on the daily average concentrations of standard atmospheric pollutants, namely carbon monoxide (CO, mg/m3), nitrogen dioxide (NO2, µg/m3), sulfur dioxide (SO2, µg/m3), ozone (O3, µg/m3), and particulate matter (PM10 and PM2.5, µg/m3), and air quality index (AQI) were obtained from Tehran air quality monitoring stations. The optical depth data of the MODIS sensor (MOD04_L2) with a spatial resolution of 1 km were extracted in the Google Earth Engine (GEE) system for the statistical period under study. Finally, to examine the physical development of Tehran in the past three decades, the Landsat 7 image from 2002 (representative of the first decade), the Landsat 8 image from 2013 (representative of the second decade), and the Landsat 8 image from 2022 (representative of the third decade) were received from the site (https://earthexplorer.usgs.gov). After performing radiometric and geometric corrections, the NDBI index was calculated, and the built-up areas were separated from the natural areas through Otsu thresholding. R software version 1.4.4 was used to perform statistical analysis of the data. The normality of the distribution of variables and the calculation of descriptive statistics of the data were performed using the functions provided in the MVN package. The relationship between meteorological parameters and air pollutant concentrations was analyzed by selecting the appropriate correlation analysis method based on the data distribution (normal and abnormal), and visualization of the results from the correlation matrix, including correlation coefficients and statistical significance of the coefficients at the 99.9% and 99% confidence levels, was provided by using the corrplot package.

Results and discussion:

Over these three decades, Tehran has experienced a rapid growth trend (R= 0.97), while natural areas in the Tehran metropolitan region have diminished in proportion (R=-0.98). In line with urban expansion, the proportion of snow days with excessive intensity has decreased (R=-0.94). This decline can be attributed to increased atmospheric pollutants, greenhouse gases, and the intensity of the urban heat island, which shifts the precipitation phase in favor of rain over snow. A positive correlation (R= 0.75) with a statistically significant value (P_value= 0.007) is observed between the amount of convective precipitation and the optical depth of aerosols, indicating that the amount and intensity of convective precipitation increase with greater optical depth of aerosols. There is a significant negative correlation between air pollutants (PM2.5, PM10 AQI) and the height of the lowest cloud layer. The correlation results demonstrate that clouds interact with the urban boundary layer, absorbing polluted urban air and altering droplet size distribution, which leads to a decrease in cloud base height relative to the ground surface. Based on the output of machine learning models, PM10 particulate matter and the AQI index are considered the most significant predictor variables affecting changes in cloud base height in Tehran.

Conclusion:

Investigating the impact of urbanization on precipitation phases and patterns is crucial for supporting long-term water resource planning, ensuring the sustainability of ecosystem services, and assessing and designing infrastructure risk amid climate change. Urbanization can change the local climate by modifying land-atmosphere feedback. Solid precipitation in cities is typically lower than in non-urban areas. This decrease stems from alterations in the surface energy balance of urban areas, which, due to increased greenhouse gases and the intensity of the urban heat island effect, shift the phases of solid precipitation in favor of rain. As urbanization and urban construction grow and temperatures rise, the number of snowy days decreases. In the atmosphere of Tehran, the amount of convective precipitation has increased with the increase in the optical depth of aerosols. The factors that affect the increase in convective precipitation can be attributed to the existence of an urban heat island, the roughness of large urban surfaces, and the higher concentration of atmospheric aerosols, which simultaneously increases the occurrence and intensity of convective precipitation with increasing urbanization. In examining the relationship between pollutants and the height of the lowest cloud layer, it was also determined that the atmospheric clouds of Tehran are coupled with the urban boundary layer, absorbing polluted urban air and changing the size distribution of droplets, which leads to a decrease in the height of the cloud base relative to the ground surface.

کلیدواژه‌ها [English]

  • Urban physical expansion
  • convective precipitation
  • air pollutants
  • cloud base height
  • snowfall
  1. کهراری، پریسا؛ خالدی، شهریار؛ کیخسروی، قاسم و علوی، سید جلیل. (1404). بررسی اثرات آلاینده‌های جوی معیار و پارامترهای هواشناسی بر تغییر غلظت کربن سیاه در تهران و تبریز. مخاطرات محیط طبیعی، 14(43)، 35-58. DOI: 10.22111/jneh.2024.47935.2028.
  2. Bell, TL., Rosenfeld, KM., Kim, JM., Yoo, M., Lee,I., & Hahneberger, M. (2008) Midweek increase in U.S. summer rain and storm heights suggests air pollution invigorates rainstorms. J. Geophys. 113, D02209. doi:10.1029/2007JD008623.
  3. Beck, HE., Zimmermann, NE., McVicar, TR., Vergopolan, N., Berg, A., & Wood, EF. (2018). Present and future Koppen-Geiger climate classification maps at 1-km resolution. Scientific data, 5(1), 1-12. https://doi.org/10.1038/sdata.2018.214.
  4. Bailling, R.C., Jr. and Brazel, S.W. (1987) Diurnal variation in Ari zona monsoon precipitation frequencies. Monthly Weather Review. 115, 342–346.
  5. Bamola, S., Goswami, G., Dewan, S., Goyal, I., Agarwal, M.. Dhir, A., & Anita Lakhani, A. (2024).Characterising temporal variability of PM2.5/PM10 ratio and its correlation with meteorological variables at a sub-urban site in the Taj City. Urban Climate, 53. https://doi.org/10.1016/j.uclim.2023.101763.
  6. Birinci, E., Denizoglu, M., Ozdemir, H. et al. (2025). The role of meteorological variables and cloud base heights in urban air quality. Air Qual Atmos Health (2025). https://doi.org/10.1007/s11869-025-01822-4.
  7. Choi, YS., Ho, CH., Kim,J., Gong,DY., & Park,R.J. (2008).The impacts of aerosols on the summer rainfall frequency in China. J. Appl. MeteorClimatol, 47, 1802-1813, doi.org/10.1175/2007JAMC1745.1.
  8. Cao, Q., Yupeng, L., Matei, G., & Jianguo, W. (2020). Impacts of Landscape Changes on Local and Regional Climate: A Systematic Review. Landscape Ecology 35, 1269–90. https://doi.org/10.1007/s10980-020-01015-7.
  9. Du, Z., Li, W., Zhou, D., Tian, L., Ling, F., Wang, H., Gui, Y., & Sun, B. (2014). Analysis of Landsat-8 OLI imagery for land surface water mapping. Remote Sens. Lett, 5, 672–681.
  10. Diem, J. and Brown, D. (2003). Anthropocentric impacts on summer precipitation in central Arizona, U.S.A. The Professional Geographer, 55(3), 343–355.
  11. Farias, W., Pinto, O., Naccarato, K.P., & Pinto, I. (2009). Anomalous lightning activity over the metropolitan region of São Paulo due to urban effects. Atmos. Res, 91, 485-490.
  12. Gebremariam, S., Siwei, L., & Mengsteab, W. (2018). Observed Correlation between Aerosol and Cloud Base Height for Low Clouds at Baltimore and New York, United States, Atmosphere 9(4), 143. https://doi.org/10.3390/atmos9040143.
  13. Gu, Y., & Li, D. (2018). A modeling study of the sensitivity of urban heat islands to precipitation at climate scales. Urban Climate, 24, 982-993. https://doi.org/10.1016/j.uclim.2017.12.001.
  14. Huang, X., Wang, D., Ziegler, A. D., Liu, X., Zeng, H., Xu, Z., & Zeng, Z. (2022). Influence of urbanization on hourly extreme precipitation over China. Environmental Research Letters. 17(4)044010. doi: 10.1088/1748-9326/ac59a6.
  15. Hu, J., Liu, Y., Sang, Y. F., Liu, C., & Singh, V. P. (2021). Precipitation variability and its response to urbanization in the Taihu Lake Basin, China. Theoretical and Applied Climatology, 144, 1205-1218. https://doi.org/10.1007/s00704-021-03597-x.
  16. Intergovernmental Panel on Climate Change (IPCC). (2013). The Physical Science Basis. Contribution of Working Group I to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change. Cabbridge University Press.
  17. Kug, J. S., & Ahn, M. S. (2013). Impact of urbanization on recent temperature and precipitation trends in the Korean peninsula. Asia-Pacific Journal of Atmospheric Sciences49, 151-159, https://doi.org/10.1007/s13143-013-0016-z.
  18. Korkmaz, S., Goksuluk, D., & Zararsiz, GN. (2014). MVN: An R package for assessing multivariate normality. R Journal, 6(2).
  19. Kahrari, P., Khaledi, S., Keikhosravi, G., & Alavi, S. J. (2025). Investigating the effects of criteria air pollutants and meteorological parameters on the change of black carbon concentration in Tehran and Tabriz. Journal of Natural Environmental Hazards, 14(43), 35-58. DOI: 10.22111/jneh.2024.47935.2028. [In Persian].
  20. Kar, SK., Liou, YA., & Ha, KJ. (2007). Characteristics of cloud-to-ground lightning activity over Seoul, South Korea in relation to an urban effect. Ann. Geophys., 25, 2113-2118. https://doi.org/10.5194/angeo-25-2113-2007.
  21. Kar, SK., Liou, YA., & Ha, KJ. (2009). Aerosol effects on the enhancement of cloud-to-ground lightning over major urban areas of South Korea. Atmos.. Res., 92, 80-87. https://doi.org/10.1016/j.atmosres.2008.09.004.
  22. Koren, I., Kaufman, YJ., Rosenfeld, D., Remer, LA., & Rudich, Y. (2005). Aerosol invigoration and restructuring of Atlantic convective clouds. Geophys. Res. Lett. 32, 10–1029. doi.org/10.1029/2005GL023187.
  23. Kourtidis, K., Stathopoulos, S., Georgoulias, AK., Alexandri, G., & Rapsomanikis, SA. (2015). study of the impact of synoptic weather conditions and water vapor on aerosol–cloud relationships over major urban clusters of China. Atmos. Chem. Phys, 15, 10955–10964. doi:10.5194/acp-15-10955-2015.
  24. Lacke, MC., Mote, T.L., & Shepherd,JM. (2009). Aerosols and associated precipitation patterns in Atlanta. Atmos, 43, 4359- 4373. https://doi.org/10.1016/j.atmosenv.2009.04.022.
  25. Li, W., Du, Z., Ling, F., Zhou, D., Wang, H., & Gui, Y. (2013). A comparison of land surface water mapping using the normalized difference water index from TM, ETM+ and ALI. Remote Sens, 5, 5530–5549. doi:10.3390/rs5115530.
  26. Li, L., Zha, Y., & Wang, R. (2020). Relationship of surface urban heat island with air temperature and precipitation in global large cities. Ecological Indicators, 117, 106683. https://doi.org/10.1016/j.ecolind.2020.106683.
  27. Li, S., Joseph, E., Min, Q., & Yin, B. (2016). Multi-year ground-based observations of aerosol-cloud interactions in the mid-atlantic of the united states. Journal of Quantitative Spectroscopy & Radiative Transfer, 188, 192-199. https://doi.org/10.1016/j.jqsrt.2016.02.004.
  28. Li, S. (2017). Aerosol Indirect Effect and Cloud-base Height Observations in the North East of the United States. Int J Earth Environ Sci, 2(2), 128. doi.org/10.15344/2456-351X/2017/128.
  29. Li, Z., Niu, F., & Fan, J.  (2011). Long-term impacts of aerosols on the vertical development of clouds and precipitation. Nature Geosci, 4, 888–894. https://doi.org/10.1038/ngeo1313.
  30. Meng, K., Cheng, X., Xu, X., Qu, X., Ma, C., Zhao, Y., ... & Ding, G. (2017). Spatial-temporal variations of pollutant emission sources inverted by adaptive nudging scheme over Beijing-Tianjin-Hebei region based on the CMAQ model. Acta Scientiae Circumstantiae, 37(1), 52-60. DOI: 10.1016/j.scitotenv.2018.06.021.
  31. Mishra, P., Pandey, CM., Singh, U., Gupta, A., Sahu, C., & Keshri, A. (2019). Descriptive statistics and normality tests for statistical data. Annals of cardiac anaesthesia, 22(1). https://doi.org/10.4103/aca.ACA_157_18.
  32. Naccarato, KP., Pinto,O., & Pinto,IRCA. (2003). Evidence of thermal and aerosol effects on the cloud-to-ground lightning density and polarity over large urban areas of Southeastern Brazil. Geophys. Res, https://doi.org/10.1029/2003GL017496.
  33. Otsu, N. (1979). A threshold selection method from gray-level histograms. IEEE Trans. Syst. Man Cybern, 9, 62–66.
  34. Oke, Timothy R., Gerald M., Andreas, Ch., & James A. V. (2017). Urban Climates. Cambridge: Cambridge University Press. https://doi.org/10.1016/s0168- 6321(06)80036-2.
  35. Ronald, C., & Estoque, YM. (2015). Classification and change detection of built-up lands from Landsat-7 ETM+ and Landsat-8 OLI/TIRS imageries: A comparative assessment of various spectral indices. Ecological Indicators, 56, 1470, https://doi.org/10.1016/j.ecolind.2015.03.037.
  36. Soriano, L. R., & Pablo,F. (2002). Effect of small urban areas in central Spain on the enhancement of cloud-to-ground lightning activity. Atmos. Environ. 36, 2809-2816. https://doi.org/10.1016/S1352-2310(02)00204-2.
  37. Steiger, SM., & Orville, RE. (2003). Cloud-to-ground lightning enhancement over Southern Louisiana. Geophys. Res. Lett., 30, 1975. doi:10.1029/2003GL017923.
  38. Steensen, B. M., Marelle, L., Hodnebrog, Ø., & Myhre, G. (2022). Future urban heat island influence on precipitation. Climate Dynamics, 58(11–12), 3393–3403. https://doi.org/10.1007/s00382-021-06105-z.
  39. Shepherd, J.M. (2006). Evidence of urban-induced precipitation variability in arid climate regions. Journal of Arid Environments, 67 (2006), 607–628. https://doi.org/10.1016/j.jaridenv.2006.03.022.
  40. Savic, S., Kalfayan, M., & Dolinaj, D. (2020). Precipitation spatial patterns in cities with different urbanisation types: Case study of Novi Sad (Serbia) as a medium-sized city. Geographica Pannonica24(2). doi:10.5937/gp24-25202.
  41. Song, Y., Liu, H., Wang, X., Zhang, N., & Sun, J. (2016). Numerical simulation of the impact of urban non-uniformity on precipitation. Advances in Atmospheric Sciences, 33, 783-793, https://doi.org/10.1007/s00376-016-5042-1.
  42. UN-DESA. (2018). World urbanization prospects: The 2018 revision. online edition (Tech. Rep.). United Nations. Department of Economic andSocial Affairs.
  43. Wei, T. & Simko, VR. (2021). Package “Corrplot”: Visualization of a Correlation Matrix (Version 0.92). Package Corrplot for R Software.
  44. Wang, J., Feng, J., Wu, Q., & Yan, Z. (2016). Impact of anthropogenic aerosols on summer precipitation in the Beijing–Tianjin–Hebei urban agglomeration in China: Regional climate modeling using WRF-Chem. Advances in Atmospheric Sciences, 33, 753-766. https://doi.org/10.1007/s00376-015-5103-x.
  45. https:// data.irimo.ir.
  46. https:// air.tehran.ir.
  47. https:// earthexplorer.usgs.gov.