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NTIS 바로가기한국대기환경학회지 = Journal of Korean Society for Atmospheric Environment, v.32 no.6, 2016년, pp.603 - 612
김종호 (한서대학교 환경공학과) , 황인조 (대구대학교 환경공학과)
The objective of this study was to estimate the emission characteristics for PM,
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핵심어 | 질문 | 논문에서 추출한 답변 |
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발생원에서 배출되는 먼지 중 응축성 먼지는 무엇인가? | 5로 나누어 측정한다. 응축성 먼지는 굴뚝에서 배출된 배기가스가 굴뚝 근처에서 수초 이내에 액체 혹은 고체 입자로 응축되는 물질로서 가스의 냉각과정에서 균일(homogeneous) 혹은 불균일(heterogeneous) 반응으로 생성되며, 대부분 CPM2.5로 알려져 있다 (Corio andSherwell, 2000). | |
대부분의 국가에서 PM10과 PM2.5에 대한 배출허용기준이 설정되지 않는 이유는? | 그러나 PM10과 PM2.5에 대해서는 그 위해성에 비해 배출허용기준이 대부분의 국가에서 설정되지 않은 실정인데, 이는 발생원에서 배출되는 먼지의 크기에 대한 기초자료가 부족한 것이 그 이유 중에 하나라고 보고되고 있다(Ehrlich et al., 2007). | |
대기 중의 미세입자가 대기환경에 미치는 영향은? | ,2010; Pacyna, 2010). 또한 대기환경에는 시정거리 감소(visibility impairment)를 일으킬 수 있고, 구름의 응결핵으로 작용하여 기상이변을 야기할 수도 있는 것으로 보고되고 있다(Minguillon et al., 2013; Hobbs,1993). |
Chow, J.C. (1995) Measurement methods to determine compliance with ambient air quality standards for suspended particles, Journal of Air and Waste Management Association, 45(5), 320-382.
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Corio, L.A. and J. Sherwell (2000) In-stack condensable particulate matter measurement and issues, Journal of Air and Waste Management Association, 50(3), 207-218.
Ehrlich, C., G. Noll, W.-D. Kalkoff, G. Baumbach, and A. Dreiseidler (2007) $PM_{10},\;PM_{2.5}\;and\;PM_{1.0}$ -Emissions from industrial plants-Results from measurement programmes in Germany, Atmospheric Environment, 41, 6236-6254.
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Meij, R. and H. te Winkel (2004) The emission and environmental impact of $PM_{10}$ and trace elements from a morden coal-fired power plant equipped with ESP and wet FGD, Fuel Processing Technology, 85, 641-656.
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Ministry of Environment (MOE) (2015), Enforcement Rule of the Clean Air Conservation ACT.
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National Institute of Environmental Research (NIER) (2013) A Study on the Speciation and Control Measures of $PM_{2.5}$ from Large Stationary Emission Source.
National Institute of Environmental Research (NIER) (2015a) Air Pollutants Emission Factors.
National Institute of Environmental Research (NIER) (2015b) Fine Particulate Matter (PM-10 and PM-2.5) in Flue Gas.
National Institute of Environmental Research (NIER) (2016) National Air Pollutants Emission 2013.
Oravisjarvi, K., M. Pietikainen, J. Ruuskanen, S. Niemi, M. Lauren, A. Voutilainen, R.L. Keiski, and A. Rautio (2014) Diesel particle composition after exhaust after-treatment of an off-road diesel engine and modeling of deposition into the human lung, Journal of Aerosol Science, 69, 32-47.
Pacyna, J.M., K. Sundseth, E.G. Pacyna, W. Jozewicz, J. Munthe, M. Belhaj, and S. Astrom (2010) An assessment of costs and benefits associated with mercury emission reductions from major anthropogenic sources, Journal of Air and Waste Management Association, 60, 302-315.
Pio, C., M. Cerqueira, R.M. Harrison, T. Nunes, F. Mirante, C. Alves, C. Oliveira, A.S. Campa, B. Artinano, and M. Matos (2011) OC/EC ratio observations in Europe: Re-thinking the approach for apportionment between primary and secondary organic carbon, Atmospheric Environment, 45(34), 6121-6132.
Plaza, J., B. Artinano, P. Salvador, F.J. Gomez-Moreno, M. Pujadas, and C.A. Pio (2011) Short-term secondary organic carbon estimations with a modified OC/EC primary ratio method at a suburban site in Madrid (Spain), Atmospheric Environment, 45(15), 2496-2506.
Seo, S.J., Y.K. Seo, Y.J. Hwang, D.H. Jung, and S.O. Back (2014) Application of adsorption sampling and thermal desorption with GC/MS analysis for the measurement of low-molecular weight PAHs in ambient air, Journal of Korean Society for Atmospheric Environment, 30(4), 362-377. (in Korean with English abstract)
US EPA (2014) Method 201A-Determination of $PM_{10}$ and $PM_{2.5}$ emissions from stationary sources (https://www3.epa.gov/ttn/emc/method201a.html).
US EPA (2016) SPECIATE Ver. 4.4, https://www.epa.gov/ttn/chief/software/speciate
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