• 제목/요약/키워드: ISCST3

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지역분할방법에 의한 ISCST3모델로 수도권지역에서 $SO_2$ 농도 예측 연구 (A Study on the Prediction of $SO_2$ Concentrations by a Regional Segment ISCST3 Model in the Seoul Metropolitan Area)

  • 구윤서;전경석;최한영;신봉섭;신동윤;이정주
    • 한국대기환경학회:학술대회논문집
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    • 한국대기환경학회 1999년도 추계학술대회 논문집
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    • pp.407-408
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    • 1999
  • 본 연구에서는 서울, 인천, 수원을 포함한 수도권 전지역을 대상으로 SO$_2$ 농도를 가우시안모델인 ISCST3(Industrial Source Complex for Short Term-3)로 예측하고자 한다. ISCST3 모델의 적용 영역이 넓으면 모델영역 내에서 기상조건이 상이하기 때문에 지금까지 이루어진 대부분의 연구들은 공간적으로 제한된 지역을 대상으로 해왔다.(중략)

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대구 달서구의 대기오염확산에 있어서 ISCST3와 AERMOD의 비교 연구

  • 성미애;김해동;박명희
    • 한국환경과학회:학술대회논문집
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    • 한국환경과학회 2006년도 추계 학술발표회 발표논문집
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    • pp.144-146
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    • 2006
  • 대기오염이 심화됨에 따라 미치는 영향에 대한 관심이 날로 증가하고 있고, 이러한 영향은 대기확산모델을 이용하여 예측하고 있다. 현재 우리나라에서 주로 사용되는 ISCST3는 우수한 모델이나 지형적 조건의 반영이 취약하다는 단점을 가지고 있다. 그래서 복잡지형인 우리나라의 경우에는 좀 더 정확한 예측을 하기에 아쉬운 감이 있다. 이러한 ISCST3의 단점을 보완하여 개발된 AERMOD는 ISCST3보다 지형적 조건의 반영이 탁월하여 본 연구의 대상지역의 경우처럼 높은 산이 자리하고 있는 지역에서 대기오염의 확산을 잘 예측할 것으로 사료된다.

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선 오염원에 의한 도로변 지역으로의 대기확산모델의 민감도 분석 - ISCST3, CALINE4 모델을 중심으로 - (Sensitivity Analysis of Air Pollutants Dispersion Model in the Road Neighboring Area Due to the Line Source -The Object on ISCST3, CALINE4 Model-)

  • 안원식;박명희;김해동
    • 한국환경과학회지
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    • 제16권6호
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    • pp.715-723
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    • 2007
  • The air pollutant emission is mainly caused by line sources in urban area. For example, the annually totaled air pollutant emission is known to consist of about 80% of line sources in Daegu. Hence, the appropriate assessment on the air pollutants of line sources is very important for the atmospheric environmental management in urban area. In this study, we made a comparative study to evaluate suitable dispersion model for estimating the air pollution from line sources. Two air pollution dispersion models, ISCST3 and CALINE4 were the subject of this study. The results were as follows; In the assessment of air pollution model, ISCST3 was found to have 4 times higher concentration than CALINE4. In addition, actual data obtained by measurement and estimated values by CALINE4 were generally identical. The air pollution assessment based on ISC3 model produced significantly lower values than actual data. The air pollution levels estimated by ISCST3 were very low in comparison with the observational values.

시화지구에서의 ISCST3, ISCLT3 대기확산 모델의 평가 (Evaluation of ISCST3, ISCLT3 Atmospheric Dispersion Modelling in Sihwa area)

  • 이권호;김영준;조승현
    • 한국대기환경학회:학술대회논문집
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    • 한국대기환경학회 2000년도 춘계학술대회 논문집
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    • pp.356-358
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    • 2000
  • ISC3는 EPA가 권장하는 가우시안 대기확산 모델로서 일반적으로 공장 배출원으로 인한 일정 기간동안의 대기확산농도와 범위를 예측하기 위하여 사용되어진다. ISC3 모델은 다양한 점오염원, 면오염원, 등을 취급할 수 있을 뿐 아니라 building wake와 down wash 그리고 거리의 함수로써 final plum rise를 옵션으로 사용할 수 있고 단순지형이나 복합지형의 고려가 가능하다. ISC3 모델은 단순지형 장기모델인 ISCLT3와 복합지형 단기모델인 ISCST3가 있으며 모델의 수행에 있어 약간의 차이점이 있다. (중략)

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Mathematical and experimental study of hydrogen sulfide concentrations in the Kahrizak landfill, Tehran, Iran

  • Asadollahfardi, Gholamreza;Mazinani, Safora;Asadi, Mohsen;Mirmohammadi, Mohsen
    • Environmental Engineering Research
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    • 제24권4호
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    • pp.572-581
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    • 2019
  • The emission of hydrogen sulfide (H2S) from the Kahrizak landfill was studied. Firstly, the field measurements were conducted in the summer and winter seasons; and the samples were analyzed using Jacob method. We predicted the H2S concentrations in the downwind using AERMOD and ISCST3. According to the AERMOD, the maximum concentration of H2S in the summer and winter were 117 ㎍/㎥ and 205 ㎍/㎥ respectively. The downwind concentrations reached zero at the distance of 35 km from the leachate treatment plant. The Geometric mean bias, Geometric variance, Fractional bias, Fraction of predictions within a factor of two of the observations and Normalized mean square error for the AERMOD were 0.58, 1.35, -0.12, 1.91 and 0.042, respectively in the summer and 1.39, 1.35, -0.05, 1.46 and 0.027 in the winter; and for the ISCST3, were 0.85, 1.03, 0.02, 1.45 and 0.04 in the summer and 1.18, 1.03, 0.15, 1.16 and 0.04 in the winter. The results of the AERMOD were compared with the ISCST3 and indicated that the AERMOD performance was more suitable than the ISCST3.

ISCST에 의한 하동 지역의 대기오염 확산 모델링 (Modeling on the Dispersion of Air Pollutants of Hadong area by ISCST)

  • 천성남;박민석;백점인;이태원
    • 한국대기환경학회:학술대회논문집
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    • 한국대기환경학회 2001년도 추계학술대회 논문집
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    • pp.397-398
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    • 2001
  • 대형 석탄화력 발전소에서는 발전소 가동으로 인해 발생되는 주변 오염농도를 평가하기 위하여 주기적으로 현장조사를 실시하고 있다. 본 연구에서는 미국 환경보호청(EPA) 권장 모델중 하나인 ISCST-3를 이용하여 하동화력본부 주변의 확산 모델링을 수행하여 최고 농도 발생 지점을 조사하였고 환경 기준치와의 비교결과를 나타내었다. 또한 현장에서의 실제 조사결과와 비교하여 국내 지형 및 농촌지역에의 ISC-3의 적용성을 조사하였다. (중략)

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지역 분할 방법에 의한 ISCST3 모델링으로 수도권 지역에서 SO2 농도 예측 연구 (A Study on the Prediction of SO2 Concentrations by the Regional Segment ISCST3 Modeling in the Seoul Metropolitan Area)

  • 구윤서;김성태;신봉섭;신동윤;이정주
    • 환경영향평가
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    • 제12권4호
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    • pp.245-257
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    • 2003
  • $SO_2$ concentrations in the Seoul Metropolitan Area (SMA) were predicted by the regional segment ISCST3 modeling. The SMA was segmented by three modeling regions where the weather monitoring station exists since the area of the SMA, approximately $100km{\times}100km$, is too wide to be modeled by one modeling domain. The predicted concentrations by the model were compared with the measured concentrations at 39 air monitoring stations located in the SMA to validate the ISCST3 modeling coupled with the regional segment approach. The predicted concentrations by the regional segment method showed better performance in depicting the measurements than those by the non-segment ISCST3 modeling. The correction methods of the calculated concentrations reviewed were here the correlation method by the first order linear equation and the ratio method of observed to calculated concentrations. The corrected concentrations by two methods showed good agreement with the measured data. The ratio method was, however, easily applicable to the concentration correction in case of a wide modeling region considered in this study.

보령화력 지역의 복잡지형이 대기확산 모델링에 미치는 영향 비교 (Comparison of Complex Terrain Effects in the Air Dispersion Modeling at the Poryong Power Plant Site)

  • 오현선;김영성;김진영;문길주;홍욱희
    • 한국대기환경학회지
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    • 제13권6호
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    • pp.427-437
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    • 1997
  • Complex terrain which is rather typical topographic character in Korea would greatly influence the dispersion of air pollutant. In this study, we investigated how the complex terrain in the vicinity of the coal-fired plant affects the air dispersion modeling results by using several US EPA models: SCREEN, CTSCREEN, ISCLT3, ISCST3, and RTDM. Screening analysis was followed by long-term analysis, and the plume movement over the terrain was precisely tracked for selected cases. Screening analysis revealed that the highest concentration of sulfur dioxide occurs at the downwind distance of 1.3 km under the unstable conditions with weak winds. However, this highest level of $SO_2$ could be raised by 4 times even in the presence of a hill of 170 m at a distance of 2 to 3 km. Seasonal and annual average concentrations predicted with the ISCLT3, ISCST3, and RTDM models showed a rapid incrase of $SO_2$ levels in front of the high mountains which are located more than 15 km away fromt the source. The highest concentrations predicted with ISCST3 were significantly higher than those with ISCLT3 and RTDM mainly because ISCST3 chooses simple-terrain model calculations for receptors between stack height and plume height. Although the highest levels under the stable conditions were usually found in the areas beyond 15 km or more, their absolute values were not so high due to enough dispersion effects between the source and the receptors.

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입력변수의 조건에 따른 대기확산모델의 민감도 분석 (Sensitivity Analysis of the Atmospheric Dispersion Modeling through the Condition of Input Variable)

  • 정진도;김장우;김정태
    • 한국환경과학회지
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    • 제14권9호
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    • pp.851-860
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    • 2005
  • In order to how well predict ISCST3(lndustrial Source Complex Short Term version 3) model dispersion of air pollutant at point source, sensitivity was analysed necessary parameters change. ISCST3 model is Gaussian plume model. Model calculation was performed with change of the wind speed, atmospheric stability and mixing height while the wind direction and ambient temperature are fixed. Fixed factors are wind direction as the south wind(l80") and temperature as 298 K(25 "C). Model's sensitivity is analyzed as wind speed, atmospheric stability and mixing height change. Data of stack are input by inner diameter of 2m, stack height of 30m, emission temperature of 40 "C, outlet velocity of 10m/s. On the whole, main factor which affects in atmospheric dispersion is wind speed and atmospheric stability at ISCST3 model. However it is effect of atmospheric stability rather than effect of distance downwind. Factor that exert big influence in determining point of maximum concentration is wind speed. Meanwhile, influence of mixing height is a little or almost not.