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Temporal characteristics of inhalable mercury and arsenic aerosols in the urban atmosphere in southern Taiwan

机译:台湾南部城市大气中可吸入汞和砷气溶胶的时间特征

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Urban aerosol samples for PM_(10) and PM_(2.5) were collected during summer (August) and winter (December) 2000 in southern Taiwan (Tainan City) to demonstrate the temporal variations of Hg and As in particulate matter (PM). The mean mass concentrations with standard deviations were 80.0 + 26.8 μg m~(-3) for PM_(10) and 50.6+ 16.6 μg m~(-3) for PM_(2.5). The average PM_(2.5)/PM_(10) mass ratio for the two periods combined was 63%, indicating that fine particles were a large portion of PM_(10). Particulate samples of Hg and As were analyzed within 2 days following sampling and weighing, because of the highly volatile nature of PM Hg and As. The average Hg and As values in PM_(10), PM_(2.5) and PM_(2.5-10) in summer were significantly lower than those in winter. PM_(2.5) Hg constituted 0.34 to 5.8 ng m~(-3) and PM_(2.5) 10 Hg 0.05 to 3.1 ng m~(-3). PM_(2.5) As constituted 1.09 to 9.51 ng m~(-3) and PM_(2.5-10) As 0.18 to 4.14 ng m~(-3). In summer and winter PM_(10), the Hg contents showed regular daily variation, with the higher values at daytime and lower values at nighttime, indicating conversion of gaseous Hg to the particulate phase by reaction with atmospheric oxidants under strong solar radiation during the daytime in both summer and winter. PM As behaved similar to Hg in the summer, but in the winter higher concentrations were observed during the nighttime than during the daytime, implying that the stable temperature inversion during winter nighttime caused the accumulation of PM As near the ground. In summer, SE-WSW winds carried As from an As-emitting fossil power plant to the sample area. In a similar vein, NE-WNW winter winds contributed to aerosol Hg, especially in PM_(2.5), originating from a waste incinerator located NW of Tainan City.
机译:在台湾南部(台南市)于2000年夏季(八月)和冬季(十二月)于2000年夏季(八月)和冬季(十二月)采集了PM_(10)和PM_(2.5)的城市气溶胶样品,以证明颗粒物(PM)中Hg和As的时间变化。 PM_(10)的平均质量浓度为标准偏差为80.0 + 26.8μgm〜(-3),PM_(2.5)的平均质量浓度为50.6+ 16.6μgm〜(-3)。组合的两个时期的平均PM_(2.5)/ PM_(10)质量比为63%,表明细颗粒是PM_(10)的很大一部分。由于PM Hg和As的高度挥发性,因此在采样和称重后2天内分析了Hg和As的颗粒样品。夏季PM_(10),PM_(2.5)和PM_(2.5-10)的平均Hg和As值显着低于冬季。 PM_(2.5)Hg构成0.34至5.8 ng m〜(-3)和PM_(2.5)10 Hg 0.05至3.1 ng m〜(-3)。 PM_(2.5)As为1.09至9.51 ng m〜(-3),PM_(2.5-10)As为0.18至4.14 ng m〜(-3)。在夏季和冬季PM_(10)中,Hg含量表现出规律的每日变化,白天的汞含量较高,而夜间的汞含量较低,这表明白天在强烈的太阳辐射下,气态Hg通过与大气氧化剂反应转化为颗粒相在夏季和冬季。在夏季,PM As的行为类似于汞,但在冬季,夜间的浓度高于白天,这表明冬季夜间温度的稳定反转导致了PM As在地面附近的积累。夏季,SE-WSW风将As从一个排放As的化石发电厂运送到样本区域。类似地,NE-WNW的冬季风造成了气溶胶汞,尤其是在PM_(2.5)中,这是由位于台南市西北部的垃圾焚化炉产生的。

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