利用ADMS模型调查阿拉克市现有和在建行业对空气质量的影响

Jalil Badamfirooz, A. Rahmati, Nooshin Daneshpajooh, Roya Mousazadeh, R. Mirzaei
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引用次数: 0

摘要

利用ADMS模型调查阿拉克市现有和在建行业对空气质量的影响。环境科学学报,20(1):21-40。结果与讨论:结果显示,各监测站CO、so2、no2浓度均在DoE公布的允许范围内。城市悬浮粒子(等高线)在盛行风和半盛行风方向向西和西南扩散,扩散半径可达3 km。沙赞的背景浓度为:盛行风方向向西半径1公里,半盛行风方向向西南半径5公里,直至达到19.1 μg。沙赞污染中心的so2等高线向西和向西南分别以7 km和10 km的半径聚集。no2等高线的积累量与no2相同。CO气体的影响半径从Arak扩展到Shazand。阿拉克地区CO等高线在西部和西南方向的积累半径可达5 km。沙赞地区向西、东南、西南方向的h2s等高线聚集半径可达5 km。一般来说,抽样结果与模拟结果之间的差异表明,模型中没有观察到的污染源超出了工厂排放的污染源。在大多数台站,模拟和直接监测的so2浓度差异不大,数据的相关系数较高,表明计算的准确性和工业对这种气态污染物排放的突出作用。此外,在大多数站点中,二氧化氮的环境测量结果低于模型值,这表明工业在该气体的排放中所占的份额更大。对这一排放量的高估可能是由于模型中包含了在建行业。各站环境CO浓度均高于模拟值。该污染物在污染负荷中所占份额较小,而在城市地区,CO浓度取决于移动源和交通负荷。结论:总体而言,城市污染水平表现为污染中心位于阿拉克市东南部和炼油厂、石化公司和火力发电厂的综合体。根据覆盖的排放等高线,建议在每个时期将最接近污染中心的若干点(14个点)作为关键站点,两个点作为控制站点,4个点作为暴露于污染的站点。
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Investigating the impact of existing and under construction industries on the air quality of Arak City using ADMS model
Investigating the impact of existing and under construction industries on the air quality of Arak City using ADMS model. Environmental 20(1): 21-40. Results and discussion: The results showed that the concentration of CO, SO 2 , and NO 2 in all stations was within the permissible level announced by the DoE. The dispersion of suspended particles (contour lines) in the city was to the west and southwest and up to a radius of 3 km in the prevailing and semi-prevailing wind direction. This for Shazand was to the west up to a radius of 1 km in the prevailing wind direction and to the southwest up to 5 km in the direction of semi- prevailing wind until reaching the background concentration of 19.1 μg. Accumulation of SO 2 contour lines in Shazand pollution center was observed up to a radius of 7 km in the west direction and up to a radius of 10 km in the southwest direction. The accumulation of NO 2 contour lines was the same as NO 2 . The radius of impact of CO gas was extended from Arak to Shazand. Accumulation of CO contour lines in Arak was up to a radius of 5 km in the direction of west and southwest. The accumulation of H 2 S contour lines in Shazand was up to a radius of 5 km towards the directions of west, southeast, and southwest. In general, the difference between the sampling and modeling results indicated the pollution sources that were not observed in the model and were beyond those emitted from the factories. In most stations, the modeled and directly monitored SO 2 concentrations were not much different and the correlation coefficient of the data was high, indicating the accuracy of the calculations and the prominent role of industries in the emission of this gaseous pollutant. Also, in most stations, the results of environmental measurement of NO 2 were less than the modeled values, revealing that the industries had a greater share in the emission of this gas. The overestimation of this emission may probably be due to the inclusion of the under-construction industries in the model. The environmental concentration of CO in all stations was higher than the modeled values. small share in the pollution load of this pollutant while in urban areas, the concentration of CO depends on the mobile sources and traffic load. Conclusion: In general, the pollution levels of the city showed that the center of pollution was in the southeast of Arak and in the complex of the refinery, petrochemical company, and thermal power plant. According to the overlaid contours of emissions, a number of points (14 points) that were closest to the pollution centers were proposed as critical stations, two points as control stations, and 4 points as the stations exposed to pollution in each period.
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