Dergiler / Atmospheric Pollution Research / 2020 / Cilt: 11 - Sayı: 10

Temporal and spatial variations of haze and fog and the characteristics of PM2.5 during heavy pollution episodes in China from 2013 to 2018

Sayfa
1847–1856
DOI
—
🏛️Bu makalenin bibliyografik verileri ve tam metin bağlantısı DergiPark üzerinden sağlanmıştır.
DergiPark Kaydı ↗
✨

Yapay Zeka Hızlı Bakış & Çıkarımlar

AI Insight
⚡ TL;DR(1 Cümlede Hızlı Çıkarım)

The dominant haze is humid haze, which means that its occurrence and aggravation are usually related to aerosol hygroscopic growth.

📌 3 Maddede Bu Makale

🎯
Amaç & Hipotez:In recent years, the frequent occurrence of haze and fog events in East and Central China has caused a seriousreduction in atmospheric visibility and had a huge impact on human health.
📊
Temel Bulgular & Veri:Based on the relative humidity,visibility and PM2.5 concentration, the occurrence frequencies of haze as well as the spatial and temporal variations of fog, haze and mist in China from 2013 to 2018 were analyzed.
💡
Sonuç & Katkı:The dominant haze is humid haze, which means that its occurrence and aggravation are usually related to aerosol hygroscopic growth.
🔬Tür:Araştırma Makalesi
📍Kapsam:2013 Verileri
⚙️Değişkenler:Alan Parametreleri

Özet

In recent years, the frequent occurrence of haze and fog events in East and Central China has caused a seriousreduction in atmospheric visibility and had a huge impact on human health. Based on the relative humidity,visibility and PM2.5 concentration, the occurrence frequencies of haze as well as the spatial and temporal variations of fog, haze and mist in China from 2013 to 2018 were analyzed. The occurrence frequency of the threeweather phenomena increased from 2013 until 2016, and then decreased. Regarding seasonal distribution, hazedays are concentrated in winter, while mist often appears in spring and autumn. Clean fog mainly occurs in highmountain stations and clean areas with high relative humidity, while polluted fog is more common in denselypopulated cities. In Beijing, the proportion of clean weather increases year by year, PM2.5 in haze weather inBeijing mainly consists of organic carbon, nitrate, sulfate and other secondary aerosols. Most fog events areaccompanied by air pollution. The dominant haze is humid haze, which means that its occurrence and aggravation are usually related to aerosol hygroscopic growth.

🔖

Bu Makaleye Atıf Yap

GUO, B., WANG, Y., ZHANG, X., CHE, H., ZHONG, J., CHU, Y., CHENG, L. (2020). Temporal and spatial variations of haze and fog and the characteristics of PM2.5 during heavy pollution episodes in China from 2013 to 2018. Atmospheric Pollution Research, Cilt: 11 - Sayı: 10, 1847–1856. https://ajindex.com/articles/351597

Kaynakça (6)

  1. Che, H., Zhang, X., Li, Y., Zhou, Z., Qu, J.J., 2007. Horizontal visibility trends in China 1981-2005. Geophys. Res. Lett. 34, 1–5. https://doi.org/10.1029/2007GL031450.
  2. Che, H., Zhang, X., Li, Y., Zhou, Z., Qu, J.J., Hao, X., 2009. Haze trends over the capital cities of 31 provinces in China, 1981-2005. Theor. Appl. Climatol. 97, 235–242. https://doi.org/10.1007/s00704-008-0059-8.
  3. Che, H.C., Zhang, X.Y., Wang, Y.Q., Zhang, L., Shen, X.J., Zhang, Y.M., Ma, Q.L., Sun, J.Y., Zhang, Y.W., Wang, T.T., 2016. Characterization and parameterization of aerosol cloud condensation nuclei activation under different pollution conditions. Sci. Rep. 6, 1–14. https://doi.org/10.1038/srep24497.
  4. Deng, X., Tie, X., Wu, D., Zhou, X., Bi, X., Tan, H., Li, F., Jiang, C., 2008. Long-term trend of visibility and its characterizations in the Pearl River Delta (PRD) region, China. Atmos. Environ. Times 42, 1424–1435. https://doi.org/10.1016/j.atmosenv.2007. 11.025. Ding, Y.H., Liu, Y.J., 2014. Analysis of long-term variations of fog and haze in China in recent 50 years and their relations with atmospheric humidity. Sci. China Earth Sci. 57, 36–46. https://doi.org/10.1007/s11430-013-4792-1.
  5. Hand, J.L., Schichtel, B.A., Malm, W.C., Copeland, S., Molenar, J.V., Frank, N., Pitchford, M., 2014. Widespread reductions in haze across the United States from the early 1990s through 2011. Atmos. Environ. 94, 671–679. https://doi.org/10.1016/j. atmosenv.2014.05.062. Luan, T., Guo, X., Guo, L., Zhang, T., 2018. Quantifying the relationship between PM2.5 concentration, visibility and planetary boundary layer height for long-lasting haze and fog-haze mixed events in Beijing. Atmos. Chem. Phys. 18, 203–225. https://doi. org/10.5194/acp-18-203-2018.
  6. Malm, W.C., Day, D.E., Kreidenweiss, S.M., Collett, J.L., Lee, T., 2003. Humidity-dependent optical properties of fine particles during the big bend regional aerosol and visibility observational study. J. Geophys. Res. Atmos. 108, 1–16. https://doi.org/10. 1029/2002JD002998. Park, R.J., Jacob, D.J., Kumar, N., Yantosca, R.M., 2006. Regional visibility statistics in the United States: natural and transboundary pollution influences, and implications for the Regional Haze Rule. Atmos. Environ. 40, 5405–5423. https://doi.org/10. 1016/j.atmosenv.2006.04.059. Pui, D.Y.H., Chen, S.C., Zuo, Z., 2014. PM2.5 in China: measurements, sources, visibility and health effects, and mitigation. Particuology 13, 1–26. https://doi.org/10.1016/j. partic.2013.11.001. Quan, J