Journals / Atmospheric Pollution Research / 2018 / Cilt: 9 - Sayı: 4

A first annual assessment of air quality modeling over Lebanon using WRF/ Polyphemus

Pages
643–654
DOI
—
🏛️Bibliographic metadata and full text access for this article are provided via DergiPark.
DergiPark Record ↗
✨

AI Summary & Key Takeaways

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

The results highlight an underestimation of OC, which could relate to the sensitivity of the chemical mechanism to the temperature, the boundary conditions, or the emission inventory.

📌 3 Key Takeaways

🎯
Objective & Hypothesis:Air quality is modelled at high resolution over Lebanon (5 × 5 km) and Beirut (1 × 1 km) using the WRF/ Polyphemus modeling system for the year 2014.
📊
Key Findings & Data:The observation data collected from the recently deployed national air quality monitoring network as well as ground measurement from a long-term campaign are used to evaluate both models performance.
💡
Conclusion & Impact:The results highlight an underestimation of OC, which could relate to the sensitivity of the chemical mechanism to the temperature, the boundary conditions, or the emission inventory.
🔬Design:Modeling & Simulation
📍Scope:2014 Verileri
⚙️Variables:Domain Parameters

Özet

Air quality is modelled at high resolution over Lebanon (5 × 5 km) and Beirut (1 × 1 km) using the WRF/ Polyphemus modeling system for the year 2014. The observation data collected from the recently deployed national air quality monitoring network as well as ground measurement from a long-term campaign are used to evaluate both models performance. Statistical indicators are calculated and compared to a selection of performance criteria from the literature. Accordingly, the modelled results are satisfactory and within the range of the literature for both the meteorological parameters as well as air quality pollutants. For the meteorological model, some biases are observed for the wind components especially during winter, as better statistics are obtained during summer. As for the air quality, the model satisfied commonly used performance criteria for O3 and PM2.5. However, the model underestimates the carbon monoxide values in urban regions and overestimates sulfur dioxide and it appears that these biases results mainly from the emission inventory and the meteorology. Also, EC and OC components of PM2.5 are evaluated. The results highlight an underestimation of OC, which could relate to the sensitivity of the chemical mechanism to the temperature, the boundary conditions, or the emission inventory.

🔖

Cite This Article

ABDALLAH, C., AFİF, C., MASRİ, N. E., ÖZTÜRK, F., KELEŞ, M., SARTELET, K. (2018). A first annual assessment of air quality modeling over Lebanon using WRF/ Polyphemus. Atmospheric Pollution Research, Cilt: 9 - Sayı: 4, 643–654. https://ajindex.com/articles/212565

📄 Full Text PDF Viewer

📄

PDF görüntüleyici hazırlanıyor...

References (7)

  1. Abdallah, C., Sartelet, K., Afif, C., 2016. Influence of boundary conditions and anthropogenic emission inventories on simulated O3 and PM2.5 concentrations over Lebanon. Atmos. Pollut. Res. 7 (6), 971–979. http://dx.doi.org/10.1016/j.apr.2016. 06.001. Afif, C., Dutot, A., Jambert, C., Abboud, M., Adjizian-Gérard, J., Farah, W., Perros, P., Rizk, T., 2009. Statistical approach for the characterization of NO2 concentrations in Beirut. Air Qual. Atmos. Health 2, 57–67. http://dx.doi.org/10.1007/s11869-009- 0034-2.
  2. Anderson, J.O., Thundiyil, J.G., Stolbach, A., 2012. Clearing the air: a review of the effects of particulate matter air pollution on human health. J. Med. Toxicol. 8, 166–175. http://dx.doi.org/10.1007/s13181-011-0203-1.
  3. Badaro-Saliba, N., Adjizian-Gerard, J., Zaarour, R., Abboud, M., Farah, W., Saliba, A.N., Shihadeh, A., 2014. A geostatistical approach for assessing population exposure to NO2 in a complex urban area (Beirut, Lebanon). Stoch. Env. Res. Risk Assess. 28 (3), 467–474. http://dx.doi.org/10.1007/s00477-013-0765-3.
  4. Badia, A., Jorba, O., 2015. Gas-phase evaluation of the online NMMB/BSC-CTM model over Europe for 2010 in the framework of the AQMEII-Phase2 project. Atmos. Environ. 115, 657–669. http://dx.doi.org/10.1016/j.atmosenv.2014.05.055.
  5. Baldasano, J.M., Pay, M.T., Jorba, O., Gassó, S., Jiménez-Guerrero, P., 2011. An annual assessment of air quality with the {CALIOPE} modeling system over Spain. Sci. Total Environ. 409, 2163–2178. http://dx.doi.org/10.1016/j.scitotenv.2011.01.041.
  6. Balzarini, A., Angelini, F., Ferrero, L., Moscatelli, M., Perrone, M.G., Pirovano, G., Riva, G.M., Sangiorgi, G., Toppetti, A.M., Gobbi, G.P., Bolzacchini, E., 2014. Sensitivity analysis of PBL schemes by comparing WRF model and experimental data. Geosci. Model Dev. Discuss. 7, 6133–6171. http://dx.doi.org/10.5194/gmdd-7-6133-2014.
  7. Banks, R.F., Tiana-Alsina, J., Baldasano, J.M., Rocadenbosch, F., Papayannis, A., Solomos, S., Tzanis, C.G., 2016. Sensitivity of boundary-layer variables to {PBL} schemes in the {WRF} model based on surface meteorological observations, lidar, and radiosondes during the HygrA-CD campaign. Atmos. Res. 176–177, 185–201. http://dx.doi.org/ 10.1016/j.atmosres.2016.02.024. Beegum, S.N., Gherboudj, I., Chaouch, N., Couvidat, F., Menut, L., Ghedira, H., 2016. Simulating aerosols over Arabian Peninsula with CHIMERE: sensitivity to soil, surface parameters and anthropogenic emission inventories. Atmos. Environ. 128, 185–197. http://dx.do