• 한국대기환경학회지
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• 제20권4호
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• pp.539-553
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• 2004

Up to the present time, many methods to estimate emissions from a particular diesel engines have wholly depended on the quantity of diesel fuel consumed. Then, the recommended emission factors were normalized by fuel consumption, and further total activity was estimated by the total fuel consumed. One of main purposes in the study is newly to develop emission factors for the railroad diesel rolling stock (RDRS) and to estimate a total amount of major gaseous pollutants from the RDRS in Korea. Prior to develop a Korean mode emission factor. the emission factor from the USEPA was simply applied for comparative studies. When applying the USEPA emission factors, total exhaust emissions from the RDRS in Korea were estimated by 28,117tons of NOx, 2,832.3tons of CO, and 1,237.5tons of HC, etc in 2001. In this study, a emission factor for the RDRS, so called the KoRail mode (the Korean Railroad mode) has been developed on the basis of analyzing the driving pattern of the Gyeongbu-Line especially for the line-haul mode. Explicitly to make the site specific emission factors, many uncertainty problems concerning weighting factors for each power mode, limited emission test, incomplete data for RDRS, and other important input parameters were extensively examined. Total exhaust emissions by KoRail mode in Korea were estimated by 10,960tons of NOx, and 4,622tons of CO, and so on in the year of 2001. The emissions estimated by the USEPA mode were 2.6 times higher for NOx, and 1.6 times lower for CO than those by the KoRail mode. As a conclusion, based on the emission calculated from both the USEPA mode and the KoRail mode, the RDRS is considered as one of the significant mobile sources for major gaseous pollutants and thus management plans an(1 control strategies for the RDRS must be established to improve air quality near future in Korea.

• 한국대기환경학회지
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• 제30권3호
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• pp.251-260
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• 2014

Biomass burning is one of the significant emission source of PM and CO, but a few studies are reported in Korea. Air pollutants emission from biomass burning such as wood stove and boiler, and wood-pellet stove and boiler were estimated in this study. Activity levels related to biomass burning such as fuel types, amount of fuel loading, and location and temporal variation were investigated by field survey over Korea. Fuel loadings were 14.9 kg/day for wood stove, 31.3 kg/day for wood boiler, 12.8 kg/day for wood-pellet stove, 32.5 kg/day for wood-pellet boiler during the season of active use. These were mostly burned in winter season from october to april of next year. Estimated annual emissions from wood stove & boiler were CO 76,677, $NO_x$ 710, $SO_x$ 70, VOC 20,941, TSP 6,605, PM10 2,921, PM2.5 1,851, and NH3 7 ton/yr, respectively. Emissions from wood-pellet stove and boiler were CO 32,798, $NO_x$ 1,830, $SO_x$ 25, VOCs 5,673, TSP 629, PM10 457, PM2.5 344, and $NH_3$ 2 ton/yr, respectively. When the emission estimates are compared with total emissions of the national emission inventory (CAPSS: Clean Air Policy Support System), Those occupy 12.5%, 2.8% of total national emission for CO and PM10, respectively. These results show wood and wood-pellet burning appliances were one of the major source of air pollution in Korea. In future, these types of heaters need to be regulated to reduce air pollution, especially in suburb area.

• 한국대기환경학회지
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• 제31권5호
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• pp.430-436
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• 2015

Numerical air quality forecasting suffers from the large uncertainties of input data including emissions, boundary conditions, earth surface properties. Data assimilation has been widely used in the field of weather forecasting as a way to reduce the forecasting errors stemming from the uncertainties of input data. The present study aims at evaluating the effect of input data on the air quality forecasting results in Korea when data assimilation was invoked to generate the initial concentrations. The forecasting time was set to 36 hour and the emissions and initial conditions were chosen as tested input parameters. The air quality forecast model for Korea consisting of WRF and CMAQ was implemented for the test and the chosen test period ranged from November $2^{nd}$ to December $1^{st}$ of 2014. Halving the emission in China reduces the forecasted peak value of $PM_{10}$ and $SO_2$ in Seoul as much as 30% and 35% respectively due to the transport from China for the no-data assimilation case. As data assimilation was applied, halving the emissions in China has a negligible effect on air pollutant concentrations including $PM_{10}$ and $SO_2$ in Seoul. The emissions in Korea still maintain an effect on the forecasted air pollutant concentrations even after the data assimilation is applied. These emission sensitivity tests along with the initial condition sensitivity tests demonstrated that initial concentrations generated by data assimilation using field observation may minimize propagation of errors due to emission uncertainties in China. And the initial concentrations in China is more important than those in Korea for long-range transported air pollutants such as $PM_{10}$ and $SO_2$. And accurate estimation of the emissions in Korea are still necessary for further improvement of air quality forecasting in Korea even after the data assimilation is applied.

• 한국토양비료학회지
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• 제49권6호
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• pp.720-730
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• 2016

Greenhouse-gas emission factors are widely used to estimate emissions arising from a defined unit of a specific activity. Such estimates are used both for international reporting to the United Nations Framework Convention on Climate Change (UNFCCC) and for myriad national and sub-national reporting purposes (for example, European Union Emissions Trading Scheme; EU ETS). As with the other so-called 'Kyoto protocol GHGs', the Intergovernmental Panel on Climate Change (IPCC) provides a methodology for national and sub-national estimation of $N_2O$ emissions, based on the sector from which the emissions arise. The objective of this study was to develop a integrated emission factor to estimate the direct $N_2O$ emission from an agricultural field cultivated with the red pepper, soy bean, spring cabbage, autumn cabbage and potato in 2010~2012. Emission factor of $N_2O$ calculated using accumulated $N_2O$ emission, N fertilization rate, and background $N_2O$ emission over three year experiment was $0.00596{\pm}0.001337kg$ $N_2O-N(N\;kg)^{-1}$. More extensive studies need to be conducted to develop $N_2O$ emission factors for other upland crops in the various regions of Korea because $N_2O$ emission is influenced by many factors including climate characteristics, soil properties, and agricultural practices.

• 한국입자에어로졸학회지
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• 제16권4호
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• pp.107-117
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• 2020

충청남도 대형사업장에서의 대기오염물질 배출이 미세먼지 농도에 미치는 영향에 대한 논란이 많다. 2019년 봄과 가을에 항공관측을 수행하여 충청남도 대형사업장 상공에서 대기오염물질 농도를 측정하였고, 이를 바탕으로 황산화물(SO2) 배출량을 산정하였다(하향식 배출량). 이를 사업장에서 제시한 배출량 자료(상향식 배출량)와 비교한 결과, 항공관측에 바탕을 둔 배출량이 더 많았다. 항공관측에 바탕을 둔 배출량은 석탄화력발전소는 1502.1 kg/hr, 제철소는 2805.5 kg/hr였다. 이는 사업장에서 밝힌 2019년 연평균 배출량보다 각각 2.5배와 2.0배 큰 값이다. 이와 같은 차이가 나는 원인을 규명하기 위해서는 관측에 바탕을 둔 하향식 배출량과 활동도에 바탕을 둔 기존의 상향식 배출량을 산정함에 있어서 보다 면밀한 검토와 개선이 필요하다. 하향식 배출량의 개선을 위해서는 관측 불확도를 줄이는 것이 중요하다. 불확도를 높이는 요소의 하나는 지상에서 항공기가 운행될 수 있는 최저 고도까지 관측을 하지 않은 것이다. 이러한 불확도를 줄이는 방법은 지상에서 관측을 수행하며, 더 나아가서는 지상과 항공기 관측 최저 고도 사이에서 드론 등의 방법을 통해 관측을 수행하는 것이다. 바람장 역시 관측 및 외삽과 내삽을 이용하여 평면 분포를 구하면 평면에 대한 적분을 이용하여 평면 전체의 플럭스를 구할 수 있어 불확도를 줄일 수 있을 것이다. 상향식 배출량의 정확도 개선을 위해서는 측정이 이루어지고 있는 굴뚝의 배출량 자료 정확도 개선과 함께, 관측이 이루어지고 있지 않은 배출구의 현황 파악이 필요하다.

• 한국기후변화학회지
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• 제6권3호
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• pp.175-184
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• 2015

In this study GC and PAS were used to calculate $N_2O$ concentration of exhaust gas from Wood Chip combustion system. Fuel supplied to the incinerator was collected and analyzed and then the analysis result was used to calculate $N_2O$ emissions. Tier 3 and Tier 4 Method were used to calculate the $N_2O$ emissions. Plant's Specific emission factor of $N_2O$ by Tier 3 Method was 0.35 kg/TJ, while default emission factor of Wood?Wood Waste proposed by 2006 IPCC G/L was 4 kg/TJ. So the $N_2O$ emission factor of this study was 3.65 kg/TJ lower compared to the IPCC G/L. The total emissions calculated by Plant's specific emission factor was 4.22 kg during the measuring period, but by Tier 4 Method it was 7.88 kg. This difference in emissions was caused by the difference of continuous measuring and intermittent sampling. It would be necessary to apply continuous measuring to calculate emissions of $Non-CO_2$ gas whose the density distribution is relatively high. However currently, according to the target management guideline of greenhouse gas and energy, the continuous measuring method to calculate greenhouse gas emission is applied only to $CO_2$. Therefore for reliable greenhouse gas emission calculation it would be necessary to apply continuous measuring to calculate $Non-CO_2$ gas emission.

• 한국대기환경학회지
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• 제23권1호
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• pp.50-63
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• 2007

The development of domestic plant specific emission factors is very important to estimate reliable national emissions management. This study, for the reason, was carried out to obtain advances emission factor for Carbon Dioxide ($CO_2$) by source-specific emission tests from the iron and steel industry sector which is well known as one of the major sources of greenhouse gases ($CO_2$). Emission factors estimated in this study were compared with those of IPCC for evaluation and they were found to be of similar level in the case of $CO_2$. There was no good information available on $CO_2$ plant specific emission factors from the iron and steel industry in Korea so far. The major emission sources of $CO_2$ examined from the iron and steel manufacturing precesses were a hot blast stove, coke oven, sintering furnace, electric arc furnace, heating furnace, and so on. In this study, the concentration of $CO_2$ from the hot blast stove process was the highest among all processes. The $CO_2$ emission factors for a ton of Steel and Iron products (using B-C oil) were estimated to be 0.315 $CO_2$ tonne (by Tier 3 method) and 4.89 $CO_2$ tonne. In addition, emission factor of $CO_2$ for heating furnace process was the highest among all process. Emission factors estimated in this study were compared with those of IPCC for evaluation and they were found to be of similar level in the case of $CO_2$.

• 한국기후변화학회지
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• 제1권1호
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• pp.51-57
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• 2010

현재 이륜차는 도시에서 주요 이동수단으로 활용되고 있다. 그러나 국내에서는 이륜차 온실가스 배출량 산정에 있어 활동도 자료가 부족하고, 국내 배출계수가 부족하여 그 배출량 산정의 불확도가 큰 실정이다. 본 연구에서는 최근 조사된 50cc 미만의 이륜차(모페드)까지 고려하여 이륜차의 배기량별 연료 소비량을 추정하였다. 또한 최근 조사된 일 주행거리를 활용하여 IPCC 산출 방법론에 따라 Tier 2와 Tier 3의 배출량을 산출하여 비교하였다. 그 결과, 2008년도 전국 이륜차 운행에 의한 온실가스 배출량은 Tier 2와 Tier 3 산출 방법에 의해 각각 2,758천 $ton-CO_2eq/yr$, 2,739천 $ton-CO_2eq/yr$으로 산출되었으며, 이는 국내 수송 부문 온실가스 배출량의 약 2.7%에 해당하는 양으로 추정되었다.

• 대한교통학회지
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• 제31권2호
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• pp.69-79
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• 2013

본 연구에서는 대기오염 물질이 대기 변화에 따라 주변 지역의 오염농도에 미치는 영향 분석에 대한 필요성과 구체적인 방법론을 제시하였다. 이에 대한 사례연구로서 경기도 포천지역 도로망을 대상으로 본 방법론을 적용하였다. 본 연구에서 제시한 방법론은 1) 교통에서 배출된 오염물질만을 고려한 확산 분석, 2) 교통에서 배출된 오염물질과 주변오염물질농도를 결합하여 분석하는 두 가지 분석 모형을 포함하고 있다. 이를 통해 교통에 의해 발생된 대기오염물질이 교통망과 교통망 주변지역에 미치는 영향을 분석하는데 유용 할 것으로 판단된다. 또한, 교통에 의해 발생된 대기오염원과 대기오염원이 인체에 미치는 영향을 본 분석에 근거하여 도로주변 고농도의 대기오염물질에 의한 위해성(危害性)을 평가하는데 유용할 것으로 판단된다.

• 한국대기환경학회지
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• 제31권1호
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• pp.72-82
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• 2015

We constructed greenhouse gas (GHG) and air pollution (AP) integrated sink/emission inventories and evaluated the environmental value for the vegetation sector in Seoul during year 2010. The data of vegetation, classified into four sectors of cultivated land, forest land, park and street tree, were obtained from Statistics Korea and Seoul City. Based on the previous studies, only $CO_2$ was chosen as GHG sink by vegetation. $NO_2$ and $SO_2$ were chosen as AP sink by vegetation, while isoprene, monoterpene, other VOC (OVOC) and NH3 were chosen as AP emission from vegetation. Estimation methodology and sink/emission factors were gathered from reports and published literatures. Estimated GHG sink by vegetation during year 2010 was 12,987,173 $tonCO_{2eq}$, of which approximately 1/4 was from pure vegetation and the remaining 3/4 from vegetation soil. AP sink and emission were estimated to be 23,309 tonAP and 2,629,797 tonAP, respectively. The analysis by administrative districts in Seoul revealed that among 25 districts, Seocho-gu, Nowon-gu, Eunpyeong-gu, Gwanak-gu and Gangbuk-gu were the major districts in GHG and AP sink/emission inventories for vegetation sector. Environmental value of vegetation as a function of GHG and AP sink, was estimated as 800 billion won, corresponding to 5% of the total cost of the forest land in Korea evaluated as a public function.