Li An-Na, Wen Tian-Xue, Hua Wei, Yang Yuan, Meng Ze, Hu Bo, Xin Jin-Yuan
School of Atmospheric Sciences, Chengdu University of Information Technology, Chengdu 610225, China.
State Key Laboratory of Atmospheric Boundary Layer Physics and Atmospheric Chemistry(LAPC), Institute of Atmospheric Physics, Chinese Academy of Sciences, Beijing 100029, China.
Huan Jing Ke Xue. 2020 Sep 8;41(9):3908-3917. doi: 10.13227/j.hjkx.201911237.
To understand the characterization and sources of carbonaceous aerosols at Mountain Dinghu, organic carbon (OC) and elemental carbon (EC) in size-resolved aerosol samples were measured at a regional background site in South China using a DRI Model 2001A analyzer. The average mass concentrations of organic carbon (OC) are (5.6±2.0) μg ·m in PM, (7.3±2.4) μg ·m in PM, and (12.8±4.0) μg ·m in PM; the average mass concentrations of elemental carbon (EC) are (2.3±1.4) μg ·min PM, (2.7±1.6) μg ·m in PM, and (3.4±1.7) μg ·m in PM. OC concentrations in PM and PM account for 43.8% and 57.0% of OC in PM, and EC concentrations in PM and PM account for 67.6% and 79.4%, respectively. OC and EC are enriched with fine particles. In PM and PM, the highest concentrations of OC and EC are measured in autumn, and the lowest concentration of OC is measured in winter and EC in summer. In PM, the highest OC concentration is measured in summer. Carbonaceous aerosols are mainly composed of OC2, EC1, OC3, and OC4. In summer, the concentration of OC3 is higher than that of EC1, suggesting that biogenic sources are dominant during summer. The concentration of EC1 in winter is the highest, indicating that the impacts of motor vehicle emissions are prominent in the local area during winter. OC and EC both show bimodal distributions in four seasons, with peaks in the size ranges of 0.43-0.65 μm for fine particles and 3.3-5.8 μm for coarse particles. In PM and PM, the sources of OC are mainly primary emissions. In PM, the highest concentration of SOC is measured in spring at (3.0±1.4) μg ·m and the lowest in winter at (1.3±1.4) μg ·m, indicating that the secondary aerosol formation is significant in spring. At the Mountain Dinghu background site, OC is mainly from coal combustion and motor vehicle emissions for fine particles and from biogenic sources for coarse particles. EC is mainly from coal combustion, motor vehicle emissions, and dust.
为了解鼎湖山碳质气溶胶的特征和来源,在中国南方一个区域背景站点,使用DRI 2001A型分析仪对粒径分辨气溶胶样品中的有机碳(OC)和元素碳(EC)进行了测量。有机碳(OC)在PM中的平均质量浓度为(5.6±2.0)μg·m,在PM中的平均质量浓度为(7.3±2.4)μg·m,在PM中的平均质量浓度为(12.8±4.0)μg·m;元素碳(EC)在PM中的平均质量浓度为(2.3±1.4)μg·m,在PM中的平均质量浓度为(2.7±1.6)μg·m,在PM中的平均质量浓度为(3.4±1.7)μg·m。PM和PM中的OC浓度分别占PM中OC的43.8%和57.0%,PM和PM中的EC浓度分别占67.6%和79.4%。OC和EC在细颗粒中富集。在PM和PM中,OC和EC的最高浓度出现在秋季,OC的最低浓度出现在冬季,EC的最低浓度出现在夏季。在PM中,OC的最高浓度出现在夏季。碳质气溶胶主要由OC2、EC1、OC3和OC4组成。夏季,OC3的浓度高于EC1,表明夏季生物源占主导。冬季EC1的浓度最高,表明冬季机动车排放对当地的影响显著。OC和EC在四个季节均呈现双峰分布,细颗粒在0.43 - 0.65μm粒径范围内出现峰值,粗颗粒在3.3 - 5.8μm粒径范围内出现峰值。在PM和PM中,OC的来源主要是一次排放。在PM中,春季测得的二次有机碳(SOC)最高浓度为(3.0±1.4)μg·m,冬季最低为(1.3±1.4)μg·m,表明春季二次气溶胶形成显著。在鼎湖山背景站点,细颗粒的OC主要来自煤炭燃烧和机动车排放,粗颗粒的OC主要来自生物源。EC主要来自煤炭燃烧、机动车排放和扬尘。