Journals / Atmospheric Pollution Research / 2016 / Cilt: 7 - Sayı: 3

Prediction of column ozone concentrations using multiple regression analysis and principal component analysis techniques: A case study in peninsular Malaysia

Pages
533–546
DOI
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AI Summary & Key Takeaways

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

These statisticalvalues indicated a very good agreement between the monthly predicted and observed O3 forPeninsular Malaysia.

📌 3 Key Takeaways

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Objective & Hypothesis:The aim of this study is to develop new algorithms of the column ozone (O3) in Peninsular Malaysia usingstatistical methods.
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Key Findings & Data:Four regression equations, denoted as O3 NEM, O3 SWM, (PCA1) O3 NEM season, and(PCA2) O3 SWM season, were developed.
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Conclusion & Impact:These statisticalvalues indicated a very good agreement between the monthly predicted and observed O3 forPeninsular Malaysia.
🔬Design:Research Article
📍Scope:Comprehensive Sample
⚙️Variables:Domain Parameters

Özet

The aim of this study is to develop new algorithms of the column ozone (O3) in Peninsular Malaysia usingstatistical methods. Four regression equations, denoted as O3 NEM, O3 SWM, (PCA1) O3 NEM season, and(PCA2) O3 SWM season, were developed. Multiple regression analysis (MRA) and principal componentanalysis (PCA) methods were utilized to achieve the objectives of the study. MRA was used to generateregression equations for O3 NEM and O3 SWM, whereas a combination of the MRA and PCA methodswere used to generate regression equations for PCA1 and PCA2. The results of the best regressionequations for the column O3 through MRA by using four of the independent variables were highlycorrelated (R ¼ 0.811 for SWM, R ¼ 0.803 for NEM) for the six-year (2003e2008) data. However, theresult of fitting the best equations for the O3 data using four of the independent variables gaveapproximately the same R values (z0.83) for both the NEM and SWM seasons using the combined MRAand PCA methods. The common variables that appeared in both regression equations were H2O vaporand NO2. This result was expected because NO2 is a precursor of O3. The correlation coefficients (R) of thevalidation for the NEM and SWM seasons were 0.877e0.888 and 0.837e0.896, respectively. These statisticalvalues indicated a very good agreement between the monthly predicted and observed O3 forPeninsular Malaysia.

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Cite This Article

TAN, K. C., LİM, H. S., JAFRİ, M. Z. M. (2016). Prediction of column ozone concentrations using multiple regression analysis and principal component analysis techniques: A case study in peninsular Malaysia. Atmospheric Pollution Research, Cilt: 7 - Sayı: 3, 533–546. https://ajindex.com/articles/351500

References (2)

  1. Abdul-Wahab, S.A., Bakheit, C.S., Al-Alawi, S.M., 2005. Principle component and multiple regression analysis in modelling of ground-level ozone and factors affecting its concentrations. Environ. Modell. Softw. 20, 1263e1271. Abdulmogith, S.S., Harrison, R.M., 2005. The use of trajectory cluster analysis to examine the long-range transport of secondary inorganic aerosol in the UK. Atmos. Environ. 39, 6686e6695. Ahammed, Y.N., Reddy, R.R., Gopal, K.R., Narasimhulu, K., Basha, D.B., Reddy, L.S.S., Rao, T.V.R., 2006. Seasonal variation of the surface ozone and its precursor gases during 2001e2003, measured at Anantapur (14.628N), a semi-arid site in India. Atmos. Res. 80, 151e164. Al-Alawi, S.M., Abdul-Wahab, S.A., Bakheit, C.S., 2008. Combining principal component regression and artificial neural networks for more accurate predictions of ground-level ozone. Environ. Modell. Softw. 20, 1263e1271. Aumann, H.H., Chahine, M.T., Gautier, C., Goldberg, M.D., Kalnay, E., McMillin, L.M., Revercomb, H., Rosenkranz, P.W., Smith, W.L., Staelin, D.H., Strow, L.L., Susskind, J., 2003. AIRS/AMSU/HSB on the Aqua mission: design, science objectives, data products, and processing systems. IEEE Trans. Geosci. Remote 41 (2), 253e264. Azid, A., Juahir, H., Toriman, M.E., Kamaruddin, M.K.A., Saudi, A.S.M., Hasnan, C.N.C., Aziz, N.A.A., Azaman, F., Latif, M.T., Zainuddin, S.F.M., Osman, M.R., Yamin, M., 2014. Prediction of the level of air pollution using principal component analysis and artificial neural network techniques: a case study in Malaysia. Water Air Soil Poll. 225, 2063.
  2. Boian, C., Kirchhoff, V.W.J.H., 2005. Surface ozone enhancements in the south of Brazil owing to large-scale air mass transport. Atmos. Environ. 39, 6140e6146. Bovensmann, H., Burrows, J.P., Buchwitz, M., Ferrick, J., Noe, S., Rozanov, V.V., Chance, K.V., Goede, A.P.H., 1999. SCIAMACHY: mission objectives and measurement modes. J. Atmos. Sci. 56, 127e150. Bracher, A., Lamsal, L.N., Weber, M., Bramstedt, K., Coldewey-Egbers, M., Burrows, J.P., 2005. Global satellite validation of SCIAMACHY O3 columns with GOME WFMDOAS. Atmos. Chem. Phys. 5, 2357e2368. Brunner, D., Staehelin, J., Maeder, J.A., Wohltmann, I., Bodeker, G.E., 2006. Variability and trends in total and vertically resolved stratospheric ozone based on the CATO ozone data set. Atmos. Chem. Phys. 6, 4985e5008. Buchwitz, M., de Beek, R., Burrows, J.P., Bovensmann, H., Warneke, T., Notholt, J., Meirink, J.F., Goede, A.P.H., Bergamaschi, P., Korner,