SANAYİ KAYNAKLI KARBONMONOKSİT SALINIMLARININ AERMOD DAĞILIM MODELİ İLE İNCELENMESİ

Bu çalışma, özellikle kış mevsimlerinde yoğun hava kirliliğinin yaşandığı Balıkesir ili için yapılmış ilk hava kalitesi modelleme çalışmasıdır. Balıkesir il merkezinde bulunan bir sanayi işletmesinden atmosferik karbonmonoksit (CO) salınımlarının kent merkezine olan olası etkileri mevcut meteorolojik ve yüzey topoğrafya özellikleri dikkate alınarak incelenmiş ve CO salınımlarına ait yeryüzü konsantrasyonlarının dağılımlarını gösteren haritalar AERMOD ile oluşturulmuştur.Elde edilen sonuçlara göre, Balıkesir ili için uzun yıllık hakim rüzgar yönü Kuzey (N) ve Kuzey-Doğu (NE)  yönlü olarak belirlenmiştir ve kaynaktan yayılan maksimum günlük 8 saatlik ortalama CO konsantrasyonu modelleme sonucuna göre 34,01 μg.m-3 olarak tahmin edilmektedir. Bu nedenle, tahmin edilen CO seviyelerinin yasal sınırları aşmadığı ve şehir merkezine olumsuz bir etkisinin olmadığı belirlenmiştir. Ayrıca incelenen kaynağa yakın kabul edilebilecek yerde tam teşekküllü bir hastanenin olması, yapılan çalışmayı daha önemli bir hale getirmektedir. Modelleme sonucuna göre, kaynaktan salınan maksimum günlük 8 saatlik ortalama CO konsantrasyonu yaklaşık 10 μg.m-3 olarak tahmin edilmiş olup, bu değerin yine aynı yönetmelikte izin verilen yasal sınırları aşmadığı tespit edilmiştir. Çalışma sonuçlarının, halkın bilinçlendirilmesine katkı sağlanması ve yerel otoriteye karar alma sürecinde öneriler sunulması da ayrıca çalışma kapsamında önem arz etmektedir.  

An Investigation of Industrial Carbon monoxide Depositions Using AERMOD Dispersion Model

This study is the first air quality modeling study for downtown Balikesir where intense air pollution levels are experienced during the winter seasons. The possible effects of atmospheric carbonmonoxide (CO) emissions from an industrial operation in downtown Balikesir were examined by taking into consideration the existing meteorological and surface topography characteristics and the maps showing the distributions of the ground level concentrations for CO releases were created by using the AERMOD.According to the results, the prevailing wind direction was determined as North (N) and North-East (NE) for Balikesir province, and the maximum daily 8-hour means of CO concentration emitted from the source was estimated as 34,01 μg.m-3 for the modeling study. For this reason, it has been determined that the modeled CO concentrations do not exceed the legal limits and there is no adverse effect on the downtown area.  In addition, the fact that, there was a full-scaled hospital that was located nearby the source. The location of hospital complex made the air quality modeling study more significant. According to the modeling result, the maximum daily 8-hour means of CO concentration released from the source was estimated to be about 10 μg.m-3 for the hospital area. It has also been determined that the modeled value for hospital does not exceed the legal limits as states in the regulation. Within the scope of the study, the obtained results are also important due to contribution to raising public awareness and also provide suggestions to local authority in decision-making process.

___

  • Abril, G.A., Diez, S.C., Pignata, M.L. ve Britch, J. (2016) Particulate matter concentrations originating from industrial and urban sources: Validation of atmospheric dispersion modeling results, Atmospheric Pollution Research, 7, 180-189. https://doi.org/10.1016/j.apr.2015.08.009
  • Alberini, A. ve Krupnick, A. (1998) Air quality and episodes of acute respiratory illness in Taiwan cities: Evidence from survey data, Journal of Urban Economics, 44(1), 68-92. doi: https://doi.org/10.1006/juec.1997.2057
  • Aneja V.P, Agarwal, A., Roelle P.A., Phillips S.B., Tong, Q., Watkins, N. ve Yablonsky R. (2001) Measurements and analysis of criteria pollutants in New Delhi, India, Environment International, 27, 35-42. https://doi.org/10.1016/S0160-4120(01)00051-4
  • Borge, R., Lumbreras, J., Perez, J., de la Paz, D. Ve Vedrenne, M. (2014) Emission inventories and modeling requirements for the development of air quality plans. Application to Madrid (Spain), Science of the Total Environment, 466, 809-819. doi: https://doi.org/10.1016/j.scitotenv.2013.07.093
  • Brunekreef, B. ve Holgate, S.T. (2002) Air pollution and health, The Lancet, 360(9341), 1233-1242. doi: https://doi.org/10.1016/S0140-6736(02)11274-8
  • Carslaw, D.C. (2015) The openair manual — open-source tools for analysing air pollution data. Manual for version 1.1-4, King’s College London.
  • Carslaw, D.C. ve K. Ropkins (2012) Openair — an R package for air quality data analysis, Environmental Modelling & Software,27-28, pp. 52–61.
  • Chang, J.C. ve Hanna, S.R. (2004) Air quality model performance evaluation, Meteorol. Atmos. Phys., 87: 167-196. doi: https://doi.org/ 10.1007/s00703-003-0070-7
  • Gokhale, S. ve Khare, M. (2005) A hybrid model for predicting carbon monoxide from vehicular exhaust in urban environments, Atmospheric Environment, 39, 4025-4040. doi:10.1016/j.atmosenv.2005.04.010
  • Gomzi, M. (1999) Indoor air and respiratory health in preadolescent children, Atmospheric Environment, 33(24-25),4081-4086. doi: https://doi.org/10.1016/S1352-2310(99)00149-1
  • Hava Kalitesi İzleme. (2018) Hava Kalitesi İzleme Ağı. Çevre ve Şehircilik Bakanlığı web sayfası. Erişim Tarihi: 25.06.2018. Konu: Balıkesir il merkezine ait CO ölçüm raporu.
  • H.K.D.Y.Y. (2008) http://cygm.csb.gov.tr/yonetmelikler-i-440. Erişim Tarihi: 26.01.2018. Konu: Hava Kalitesi Değerlendirme ve Yönetimi Yönetmeliği.
  • Helander, M. L., Savolainen, J., and Ahlholm, J. (1997) Effects of air pollution and other environmental factors on birch pollen allergens, Allergy: European Journal of Allergy & Clinical Immunology, 52(12),1207-1214. doi: https://doi.org/10.1111/j.1398-9995.1997.tb02525.x
  • Liu, C.,Yin, P., Chen, R., Meng, X., Wang, L., Niu, L., Lin, Z., Liu, Y., Liu, J., Qi, J., You, J., Kan, H. ve Zhou, M. (2018) Ambient carbon monoxide and cardiovascular mortality: a nationwide time-series analysis in 272 cities in China, The Lancet Planetary Health, 2, e12-e18. https://doi.org/10.1016/S2542-5196(17)30181-X
  • Martonen T,B., ve Schroeter, J.D. (2003) Risk assessment dosimetry model for inhaled particulate matter: I. Human subjects, Toxicology Letters, 138(1-2), 119-132. doi: https://doi.org/10.1016/S0378-4274(02)00411-3
  • Monn, C., Alean-Kirkpatrick, P., Künzli, N., Defila, C., Peeters, A., Ackermann-Liebrich, U., Leuenberger, F. and SAPALDIA Team. (1999) Air pollution, climate and pollen comparisons in urban, rural and alpine regions in Switzerland (SAPALDIA study), Atmospheric Environment, 33(15), 2411-2416. doi: https://doi.org/10.1016/S1352-2310(99)00068-0
  • Moshammer, H ve Neuberger, M. (2003) The active surface of suspended particles as a predictor of lung function and pulmonary symptoms in Austrian school children, Atmospheric Environment, 37, 1737-1744. doi: https://doi.org/10.1016/S1352-2310(03)00073-6
  • SKHKKY-EK1 (2014) http://cygm.csb.gov.tr/yonetmelikler-i-440. Erişim Tarihi: 26.01.2018. Konu: Sanayi Kaynaklı Hava Kirliliğinin Kontrolü Yönetmeliği Ek-1.
  • Tecer, L.H. (2009) A factor analysis study: Air pollution, meteorology, and hospital admissions for respiratory diseases, Toxicological & Environmental Chemistry, 91(7): 1399-1411. doi: https://doi.org/10.1080/02772240902732316
  • Timonen, K.L., Pekkanen, J., Tiittanen, P. ve Salonen, R.O. (2002) Effects of air pollution on changes in lung function induced by exercise in children with chronic respiratory sypmtoms, Occup Environ Med, 59.129-134. doi: http://dx.doi.org/10.1136/oem.59.2.129
  • USEPA, (2018) https://www.epa.gov/co-pollution, Erişim Tarihi: 26.01.2018, Konu: Carbon Monoxide (CO) Pollution in Outdoor Air.
  • Vallero, D. A. (2008) Fundementals of Air Pollution, Fourth Edition, Elsevier Academic Press, UK.
  • Visscher, A. (2014) Air Dispersion Modeling, John Wiley & Sons Press. Hoboken, New Jersey.
  • Wang, L.K., Pereria, N.C., ve Hung, Y.T. (2004) Air Pollution Control Engineering, Humana Press, Totowa, New Jersey.
  • Williams, R., Creason, J., Zweidinger, R., Watts, R., Sheldon L., ve Shy, C. (2000) Indoor, outdoor, and personal exposure monitoring of particulate air pollution: the Baltimore elderly epidemiology-exposure pilot study, Atmospheric Environment,34(24), 4193-4204. doi: https://doi.org/10.1016/S1352-2310(00)00209-0
  • Wong, G. W. K., Ko, F. W. S., Lau, T. S., Li, S. T., Hui, D., Pang, S. W., Leung, R., Fok, T. F. ve Lai, C. K. W. (2000) Temporal relationship between air pollution and hospital admissions for asthmatic children in Hong Kong, Clinical and Experimental Allergy, 31(4), 565-569. doi: https://doi.org/10.1046/j.1365-2222.2001.01063.x
  • Wordley, J., Walters, S. ve Ayres, J. (1997) Short term variations in hospital admissions and mortality and particulate air pollution, Occupational & Environmental Medicine, 54(2), 108-116. doi: http://dx.doi.org/10.1136/oem.54.2.108
Uludağ Üniversitesi Mühendislik Fakültesi Dergisi-Cover
  • ISSN: 2148-4147
  • Yayın Aralığı: Yılda 3 Sayı
  • Başlangıç: 2002
  • Yayıncı: BURSA ULUDAĞ ÜNİVERSİTESİ > MÜHENDİSLİK FAKÜLTESİ