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Effects of highway networks on ambient ozone concentrations - A case study in southern Taiwan

机译:公路网对环境臭氧浓度的影响-以台湾南部为例

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摘要

The fraction of days on which ozone concentrations exceeded the ambient air quality standard increased from 2.9% in 2000 to 4.6% in 2004 in southern Taiwan. Mobile sources attributed for 44.7% and 17.6% of the ozone precursors, NO, and NMHC, respectively, based on the emission inventory of the Taiwan EPA. However, a new second north south highway was recently constructed in Taiwan. This study evaluates how emissions from the first and second highways affect the ambient air quality, especially ozone concentration by using CMAQ between 14 and 17 December 2002. Two emissions scenarios were examined. The first involved emissions from only the first highway and the second involved emissions from only the second highway. The mean errors of the unpaired peak ozone concentration were generally less than 17%; and those of the paired ozone concentrations were less than 25%. Correspondingly, the results simulated by the model were highly consistent with observed data. Simulation results indicated that most ambient O-3 concentrations increased by more than 2ppb with hourly increments of up to 6ppb, in both scenarios. Although the total emissions were the same, the differences among emission locations were responsible for substantial differences in ozone concentrations. The ozone concentrations decreased along the highway as the emissions increased, because of NO titration. However, the ozone concentrations were greater at sites that were further downwind. Therefore, the ozone concentrations changed significantly with the highway network, given the same total emission. The differences in ozone concentrations were caused by the changes in the emission locations of NOx. (c) 2006 Elsevier Ltd. All rights reserved.
机译:台湾南部臭氧浓度超过环境空气质量标准的天数比例从2000年的2.9%增加到2004年的4.6%。根据台湾EPA的排放清单,移动源分别占臭氧前体NO,NMHC和NMHC的44.7%和17.6%。但是,台湾最近又修建了一条新的南北第二高速公路。这项研究通过使用CMAQ在2002年12月14日至17日之间评估了第一和第二条高速公路的排放如何影响环境空气质量,特别是臭氧浓度。研究了两种排放情景。第一个仅涉及第一条高速公路的排放,第二个仅涉及第二条高速公路的排放。未配对的臭氧峰值浓度的平均误差通常小于17%;而成对的臭氧浓度低于25%。相应地,模型模拟的结果与观测数据高度一致。模拟结果表明,在两种情况下,大多数环境O-3浓度均增加了2ppb以上,每小时增加了6ppb。尽管总排放量相同,但排放地点之间的差异是造成臭氧浓度存在实质性差异的原因。由于NO滴定,随着排放量的增加,沿高速公路的臭氧浓度降低。但是,在顺风处,臭氧浓度更高。因此,在总排放量相同的情况下,臭氧浓度随公路网而显着变化。臭氧浓度的差异是由NOx排放位置的变化引起的。 (c)2006 Elsevier Ltd.保留所有权利。

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