首页> 外文期刊>Aerosol and Air Quality Research >Atmospheric Deposition Modeling of Polychlorinated Dibenzo-p-dioxins, Dibenzofurans and Polychlorinated Biphenyls in the Ambient Air of Southern Taiwan. Part I. Dry Depositions
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Atmospheric Deposition Modeling of Polychlorinated Dibenzo-p-dioxins, Dibenzofurans and Polychlorinated Biphenyls in the Ambient Air of Southern Taiwan. Part I. Dry Depositions

机译:台湾南部周围空气中多氯联苯对二恶英,二苯并呋喃和多氯联苯的大气沉积模型。第一部分干法沉积

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Atmospheric deposition, including dry and wet deposition, is a primary pathway for the transfer of POPs to terrestrial and aquatic ecosystems. In this study (that is, the part I.), the characteristics of PCDD/Fs and PCBs in the ambient air of Tainan City were simulated by the PM10 versus PCDD/Fs concentration regression analysis, gas-particle partition modeling, and the simulation of dry deposition. Dry deposition fluxes are obtained from the combination of the PCDD/F and PCB concentrations, meteorological information, dry deposition velocities, and scavenging ratios. The dry deposition fluxes of PCDD/F-TEQ2005 increase with decreasing temperature, while increase with a higher degree of chlorine numbers on PCDD/F homologues. In this study (that is, the part I.), the average PCDD/F dry deposition fluxes in spring, summer, fall and winter were 69.3, 28.2, 129 and 246 pg WHO-TEQ/m2-month during 2012, respectively. As for 2013, the average PCDD/F dry deposition fluxes in spring, summer, fall and winter were 67.0, 29.8, 102 and 377 pg WHO-TEQ/m2-month, respectively. The average PCB dry deposition fluxes in spring, summer, fall and winter were 2.16, 1.99, 5.70 and 11.9 pg WHO-TEQ/m2-month during 2012, respectively. As for 2013, the average PCB dry deposition fluxes in spring, summer, fall and winter were 2.11, 1.27, 4.49 and 8.88 pg WHO-TEQ/m2-month, respectively. The minimum simulated value occurred in summer, while the maximum dry deposition fluxes, which were about 4–5 times higher than the minimum values, occurred in winter. The lower values observed in summer may be caused by the atmospheric diffusion of SVOCs and high rainfall intensity.
机译:大气沉积,包括干沉降和湿沉降,是持久性有机污染物向陆地和水生生态系统转移的主要途径。在本研究中(即第一部分),通过PM10与PCDD / Fs浓度回归分析,气固颗粒分配建模和模拟,模拟了台南市周围空气中PCDD / Fs和PCBs的特征。干沉积。干沉降通量是通过PCDD / F和PCB浓度,气象信息,干沉降速度和清除率的组合获得的。 PCDD / F-TEQ2005的干沉降通量随着温度的降低而增加,而随着PCDD / F同源物中氯含量的增加而增加。在本研究(即第一部分)中,2012年春季,夏季,秋季和冬季的平均PCDD / F干沉降通量分别为WHO-TEQ / m2月的69.3、28.2、129和246 pg WHO-TEQ / m2月。截至2013年,春季,夏季,秋季和冬季的平均PCDD / F干沉降通量分别为WHO-TEQ / m2月67.0、29.8、102和377 pg。 2012年春季,夏季,秋季和冬季,PCB的平均干沉积通量分别为WHO / TEQ / m2月的2.16、1.99、5.70和11.9 pg。截至2013年,春季,夏季,秋季和冬季的平均PCB干沉降通量分别为WHO-TEQ / m2月,2.11、1.27、4.49和8.88 pg WHO-TEQ / m2月。最小的模拟值发生在夏季,而最大的干沉降通量在冬天出现,是最小值的大约4-5倍。夏季观测到的较低值可能是由于SVOCs在大气中的扩散和高降雨强度造成的。

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