• 환경영향평가
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• 제16권4호
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• pp.277-283
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• 2007

Since the Kyoto Protocol became into effect, Korea has been expected to be part of the Annex I countries performing the duty of GHG reduction in the phase of post-Kyoto. Therefore, it is necessary to develop emission factors appropriate to Korean circumstances. In order to develop emission factors this study utilized the CleanSYS, which is the real-time monitoring system for industrial smoke stacks to calculate the emission rate of $CO_2$ continuously. In this study, the main focus was on the power generation plants emitting the largest amount of $CO_2$ among the sectors of fossil fuel combustion. Also, an examination on the comparison of $CO_2$ emission was made among 3 generation plants using the different types of fuels such as bituminous coal and LNG; one for coal and others for LNG. The $CO_2$ concentration of the coal fired plant showed Ave. 13.85 %(10,384 ton/day). The LNG fired plants showed 3.16 %(1,031 ton/day) and 3.19 %(1,209 ton/day), respectably. Consequently, by calculating the emission factors using the above results, it was found that the bituminous coal fired power plant had the $CO_2$ emission factor average of 88,726 kg/TJ, and the LNG fired power plants had the $CO_2$ average emission factors of 56,971 kg/TJ and 55,012 kg/TJ respectably which were similar to the IPCC emission factor.

• 한국대기환경학회지
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• 제33권4호
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• pp.342-350
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• 2017

We report mass concentration and size fraction of TPM, $PM_{10}$ and $PM_{2.5}$ according to Korea standard test method (ES 01301.1 and ES 01317.1) and ISO 23210 methods. Particulate matters were sampled in large stationary emission sources such as a coal power plant and B-C oil refinery. The Korea standard test method PM mass concentrations showed 3~3.5 times larger than the cascade impactor method. On the other hand, the size fraction results showed less than 5% difference (i.e. $PM_{2.5}/PM_{10}$) between two methods. Moreover, the correlation coefficient ($r^2$) is 0.84 between TPM results of the Korea standard test method and CleanSYS. These results suggested not only improvement of current test criteria in terms of technical and theoretical aspects. Further, additional measurements are required in various large stationary sources to compare current field data.

• 한국환경과학회지
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• 제28권4호
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• pp.455-464
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• 2019

BAT-AEL(Best Available Techniques Associate Emission Level) is the basis for establishing permissible emission standards for the workplace. Therefore, it is necessary to formulate a regulated BAT-AEL setting methodology that is generally applicable to all relevant industries. For the BAT-AEL settings, various factors should be considered such as the pollutants item, whether the workplace is subject to integrated pollution prevention and control, whether BAT is applicable, the basic data type, the emission classification system, and the suitability of the collected data. Among these factors, it is the most important factor to establish the classification system for the emitting facilities such that the emission characteristics of an industrial facility and its pollutants can be effectively reflected. Furthermore the target of the survey workplace should adhere to the BAT guidelines, even if it is a workplace that is subject to an the integrated environmental system. Certified data (SEMS, TMS, cleanSYS, WEMS, etc.) can be used to prioritize the classification system for the emission facility and the emission levels of pollutants. However, the self-measured data, daily logs, and questionnaire data from the workplace can also be used upon agreement of the relevant TWG. The collected data should only be used only when the facility is operating normally. Data that have been determined to be outliers or inappropriate validation methods should also be excluded. The BAT-AEL can be establish by adhering to the following procedure: 1) investigate all relevant workplaces with in the industry, 2)select workplaces for integrated management, 3)Identify BAT application, 4)identify whether BAT is generally applicable, 5)establish a classification system for emitting facilities, 6)collection available data, 7)verify conformity, 8)remove of outliers, 9)prepare the BAT-AEL draft, 10)deliberate, and 11) perform the confirmation procedure.

• 한국산학기술학회논문지
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• 제20권6호
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• pp.19-25
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• 2019

국내 산업단지에서 배출되는 대기오염물질의 모니터링을 위해 굴뚝원격감시시스템이 운영되고 있으나 대상 시설이 한정적이어서, 시스템이 설치되지 않은 시설은 단속 요원이 직접 모니터링 및 단속을 수행하고 있다. 그래서 효율적인 산업단지에서 배출되는 대기오염물질의 모니터링을 위해 다양한 센서를 활용한 연구들이 수행되고 있다. 이에 따라 본 연구에서는 초분광센서로 측정할 수 있는 분광복사량을 활용하여 대기오염물질 중 이산화질소의 농도를 추정할 수 있는 공식을 개발하고 검증하였다. 농도 추정식 개발을 위해 다양한 농도의 이산화질소를 대상으로 태양천정각, 관측천정각, 상대방위각을 다르게 하여 분광복사량을 관측하였다. 관측된 분광복사량에서 특정 파장 간의 값의 차이를 흡수 깊이로 하였으며, 흡수 깊이와 이산화질소 농도와의 관계를 이용하여 농도 추정식을 개발하였다. 그리고 개발된 농도 추정식들의 검증을 위해 이산화질소와 아황산가스가 혼합된 가스를 대상으로 측정한 분광복사량을 이용하였다. 그 결과, 추정식의 형태에 따라 결정 계수와 RMSE가 0.71~0.88, 72~323 ppm으로 나타났으며, 지수 형태의 농도 추정식의 결정 계수가 가장 높게 나타났다. 추정식의 형태에 따라 농도의 변화에 따른 추정 농도의 정확도가 일정하지 않지만, 향후 농도 추정식의 고도화가 이루어진다면 초분광 센서를 활용하여 산업단지 배출되는 이산화질소의 모니터링에 사용 가능할 것으로 판단된다.