- Volumes 84-95 (2024)
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Volumes 72-83 (2023)
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Volume 83
Pages 1-258 (December 2023)
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Volume 82
Pages 1-204 (November 2023)
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Volume 81
Pages 1-188 (October 2023)
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Volume 80
Pages 1-202 (September 2023)
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Volume 79
Pages 1-172 (August 2023)
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Volume 78
Pages 1-146 (July 2023)
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Volume 77
Pages 1-152 (June 2023)
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Volume 76
Pages 1-176 (May 2023)
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Volume 75
Pages 1-228 (April 2023)
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Volume 74
Pages 1-200 (March 2023)
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Volume 73
Pages 1-138 (February 2023)
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Volume 72
Pages 1-144 (January 2023)
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Volume 83
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Volumes 60-71 (2022)
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Volume 71
Pages 1-108 (December 2022)
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Volume 70
Pages 1-106 (November 2022)
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Volume 69
Pages 1-122 (October 2022)
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Volume 68
Pages 1-124 (September 2022)
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Volume 67
Pages 1-102 (August 2022)
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Volume 66
Pages 1-112 (July 2022)
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Volume 65
Pages 1-138 (June 2022)
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Volume 64
Pages 1-186 (May 2022)
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Volume 63
Pages 1-124 (April 2022)
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Volume 62
Pages 1-104 (March 2022)
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Volume 61
Pages 1-120 (February 2022)
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Volume 60
Pages 1-124 (January 2022)
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Volume 71
- Volumes 54-59 (2021)
- Volumes 48-53 (2020)
- Volumes 42-47 (2019)
- Volumes 36-41 (2018)
- Volumes 30-35 (2017)
- Volumes 24-29 (2016)
- Volumes 18-23 (2015)
- Volumes 12-17 (2014)
- Volume 11 (2013)
- Volume 10 (2012)
- Volume 9 (2011)
- Volume 8 (2010)
- Volume 7 (2009)
- Volume 6 (2008)
- Volume 5 (2007)
- Volume 4 (2006)
- Volume 3 (2005)
- Volume 2 (2004)
- Volume 1 (2003)
• Air quality forecasting of GRAPES-CMAQ and MM5-CMAQ was assessed.
• Both models had similar good performance with better performance by GRAPES-CMAQ.
• Underestimations of nitrate and ammonium salt contributed to underestimations of PM2.5.
• Effect of meteorological factors and physical–chemical processes on forecast results was discussed.
The community multiscale air quality (CMAQ) model was used to forecast air quality over the Pearl River Delta region from December 2013 to January 2014. The pollution forecasting performance of CMAQ coupled with two different meteorological models, i.e., the global/regional assimilation and prediction system (GRAPES) and the fifth-generation mesoscale model (MM5), was assessed by comparison with observational data. The effects of meteorological factors and physicochemical processes on the forecast results were discussed through process analysis. The results showed that both models exhibited good performance but that of GRAPES-CMAQ was better. GRAPES was superior in predicting the overall variation tendencies of meteorological fields, but it showed large deviations in atmospheric pressure and wind speed. This contributed to the higher correlation coefficients of the pollutants with GRAPES-CMAQ but with greater deviations. The underestimations of nitrate and ammonium salt contributed to the underestimations of both particulate matter and extinction coefficients. Source emissions made the only positive contributions to surface layer SO2, CO, and NO. It was found that O3 originated primarily from horizontal and vertical transport and that its consumption was predominantly via chemical processes. Conversely, NO2 was found derived primarily from chemical production.