Journals / Atmospheric Pollution Research / 2020 / Cilt: 11 - Sayı: 8

Spatial distribution and source contributions of PM2.5 concentrations in Jincheng, China

Pages
1281–1289
DOI
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AI Summary & Key Takeaways

AI Insight
⚡ TL;DR(Too Long; Didn't Read)

The results show that the CALPUFF simulation resultsunderestimate the daily average concentration of PM2.5, and the statistical analysis also reveals an underestimationtrend.

📌 3 Key Takeaways

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Objective & Hypothesis:This study investigates the spatial distribution and source contributions of fine particles (PM2.5) in complexterrain in Jincheng, China, using the Weather Research and Forecast (WRF) Model/California Puff Model(CALPUFF) modeling system.
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Key Findings & Data:To evaluate the CALPUFF performance, the simulated results were compared withthe observational data at the three monitoring stations.
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Conclusion & Impact:The results show that the CALPUFF simulation resultsunderestimate the daily average concentration of PM2.5, and the statistical analysis also reveals an underestimationtrend.
🔬Design:Modeling & Simulation
📍Scope:Comprehensive Sample
⚙️Variables:Domain Parameters

Özet

This study investigates the spatial distribution and source contributions of fine particles (PM2.5) in complexterrain in Jincheng, China, using the Weather Research and Forecast (WRF) Model/California Puff Model(CALPUFF) modeling system. To evaluate the CALPUFF performance, the simulated results were compared withthe observational data at the three monitoring stations. The results show that the CALPUFF simulation resultsunderestimate the daily average concentration of PM2.5, and the statistical analysis also reveals an underestimationtrend. The spatial distribution shows that PM2.5 concentrations decrease gradually outward from theJincheng city center. Primary PM2.5 concentrations in December are significantly higher than those in July.However, the concentrations of secondary sulfate ions (SO42−) and nitrate ions (NO3−) in July are higher thanthose in December. In December, residential heating was the main contributor to the PM2.5 concentration, accountingfor 50%, and industrial processes and dust (an anthropogenic dust from construction processes, openyards and roads) accounted for 18% and 14%, respectively.

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Cite This Article

GUO, D., WANG, R., HONG, Z. P. (2020). Spatial distribution and source contributions of PM2.5 concentrations in Jincheng, China. Atmospheric Pollution Research, Cilt: 11 - Sayı: 8, 1281–1289. https://ajindex.com/articles/351256

References (12)

  1. Abdul-Wahab, S.A., Fadlallah, S.O., 2014. A study of the effects of vehicle emissions on the atmosphere of Sultan Qaboos University in Oman. Atmos. Environ. 98, 158–167.
  2. Arunachalam, S., Wang, B., Davis, N., Baek, B.H., Levy, J.I., 2011. Effect of chemistrytransport model scale and resolution on population exposure to PM2.5 from aircraft emissions during landing and takeoff. Atmos. Environ. 45, 3294–3300.
  3. Cai, B.F., Wang, J.N., Long, Y., Li, W.X., Liu, J.G., Ni, Z., Bo, X., Li, D., Wang, J.H., Chen, X.J., Gao, Q.X., Zhang, L.X., 2015. Evaluating the impact of odors from the 1955 landfills in China using a bottom-up approach. J. Environ. Manag. 164, 206–214. CALPUFF Dispersion Model (ver.5) – a User's Guide. Earth Tech Inc, Concord, MA,USA. Choi, G.S., Lim, J.M., Lim, K.S.S., Kim, K.H., Lee, J.H., 2018. Characteristics of regional scale atmospheric dispersion around Ki-Jang research reactor using the Lagrangian Gaussian puff dispersion model. Nucl Eng Technol 50, 68–79.
  4. Cui, H.L., Yao, R.T., Xu, X.J., Xin, C.T., Yang, J.M., 2011. A tracer experiment study to evaluate the CALPUFF real time application in a near-field complex terrain setting. Atmos. Environ. 45, 7525–7532.
  5. Ghannam, K., El-Fadel, M., 2013. Emissions characterization and regulatory compliance at an industrial complex: an integrated MM5/CALPUFF approach. Atmos. Environ. 69, 156–169.
  6. Hanna, S.R., Egan, B.A., Purdum, J., Walgler, J., 2001.
  7. Evaluation of the ADMS, AERMOD, and ISC3 dispersion models with the OPTEX, duke forest, kincaid, indianapolis and lovett field datasets. Int. J. Environ. Pollut. 16, 1–6.
  8. Hoinaski, L., Franco, D., Lisboa, H.D.M., 2016. Comparison of plume lateral dispersion coefficients schemes: effect of averaging time. Atmos Pollut Res 7, 134–141.
  9. Holnicki, P., Kałuszko, A., Trapp, W., 2016. An urban scale application and validation of the CALPUFF model. Atmos Pollut Res 7 (3), 393–402.
  10. Jain, R., Vaughan, J., Heitkamp, K., Ramos, C., Claiborn, C., Schreuder, M., Schaaf, M., Lamb, B., 2007. Development of the ClearSky smoke dispersion forecast system for agricultural field burning in the Pacific Northwest. Atmos. Environ. 41, 6745–6761. Jincheng Environmental Protection Department, 2017. Jincheng's 2017 Pollution Source Emission Inventory. Kalhor, M., Bajoghli, M., 2017.
  11. Comparison of AERMOD, ADMS and ISC3 for incomplete upper air meteorological data (case study: steel plant). Atmos Pollut Res 8 (6), 1203–1208.
  12. Lee, H.D., Yoo, J.W., Kang, M.K., Kang, J.S., Jung, J.H., Oh, K.J.,