Dovehicular emissions dominate the source of C6-C8aromatics in the megacity Shanghai of eastern China?

The characteristic ratios of volatile organic compounds (VOCs) to i-pentane, the indicator of vehicular emissions, were employed to apportion the vehicular and non-vehicular contributions to reactive species in urban Shanghai. Two kinds of tunnel experiments, one tunnelwith more than 90% light duty gasoline vehicles and the otherwithmore than 60% light duty diesel vehicles, were carried out to study the characteristic ratios of vehicle-related emissions from December 2009 to January 2010. Based on the experiments, the characteristic ratios of C6-C8 aromatics to i-pentane of vehicular emissions were 0.53 ± 0.08 (benzene), 0.70 ± 0.12 (toluene), 0.41 ± 0.09 (m,p-xylenes), 0.16 ± 0.04 (o-xylene), 0.023 ± 0.011 (styrene), and 0.15 ± 0.02 (ethylbenzene), respectively. The source apportionment results showed that around 23.3% of C6-C8 aromatics in urban Shanghai were from vehicular emissions, which meant that the non-vehicular emissions had more importance. These findings suggested that emission control of non-vehicular sources, i.e. industrial emissions, should also receive attention in addition to the control of vehicle-related emissions in Shanghai. The chemical removal of VOCs during the transport from emissions to the receptor site had a large impact on the apportionment results. Generally, the overestimation of vehicular contributions would occur when the VOC reaction rate constant with OH radicals (k_OH) was larger than that of the vehicular indicator, while for species with smaller kOH than the vehicular indicator, the vehicular contribution would be underestimated by the method of characteristic ratios.     

“基金”政策下上海废弃电器电子产品处理企业管理现状及建议研究

随着中国废弃电器电子产品管理法律法规的日益完善,社会关注度和环保意识的日益提高,特别是基金补贴制度的建立,环保部门对废弃电器电子产品的管理角色正逐渐从单一的污染防治转变为对行业的综合管理.根据上海市已建立的环保、审计联合审核工作机制,通过实证研究方法对上海地区废弃电器电子产品监管现状进行深入研究,找出监管过程中存在的问题,从完善配套政策与措施,引入专业单位作为社会服务体系,促进资源化和无害化同步发展、加强培训工作四个方面提出了对策和建议.     

Diverse bacterial populations of PM2.5 in urban and suburb Shanghai,China

• Urban aerosols harbour diverse bacterial communities in Shanghai. • The functional groups were associated with nitrogen, carbon, and sulfur cycling. • Temperature, SO₂, and wind speed were key drivers for the bacterial community. Airborne bacteria play key roles in terrestrial and marine ecosystems and human health, yet our understanding of bacterial communities and their response to the environmental variables lags significantly behind that of other components of PM_2.5. Here, atmospheric fine particles obtained from urban and suburb Shanghai were analyzed by using the qPCR and Illumina Miseq sequencing. The bacteria with an average concentration of 2.12 × 10³ cells/m³, were dominated by Sphingomonas, Curvibacter, Acinetobacter, Bradyrhizobium, Methylobacterium, Halomonas, Aliihoeflea, and Phyllobacterium, which were related to the nitrogen, carbon, sulfur cycling and human health risk. Our results provide a global survey of bacterial community across urban, suburb, and high-altitude sites. In Shanghai (China), urban PM_2.5 harbour more diverse and dynamic bacterial populations than that in the suburb. The structural equation model explained about 27%, 41%, and 20%–78% of the variance found in bacteria diversity, concentration, and discrepant genera among urban and suburb sites. This work furthered the knowledge of diverse bacteria in a coastal Megacity in the Yangtze river delta and emphasized the potential impact of environmental variables on bacterial community structure.     

2010—2016年上海城区臭氧长时间序列变化特征初探

基于2010—2016年上海城区近地面大气臭氧（O₃）的连续在线观测数据，研究了上海城区O₃长时间序列变化规律和污染特征.结果表明，近7年来上海城区O₃污染逐渐凸显，但总体以轻度污染为主，7—8月高温炎热季节以中度污染居多.城区O₃-8 h（臭氧日最大8 h滑动平均）年均增速为3.81 μg·m^-3·a^-1，99%和95%分位值增速较快，分别为6.65和4.94 μg·m^-3·a^-1；25%、50%和75%分位值的增速在3.06~4.45 μg·m^-3·a^-1之间.春季O₃浓度均值较高，年际变化小；夏季极值较高，且污染超标情况最为突出；秋季O₃浓度次于春、夏季，冬季最低；夏、秋和冬季O₃浓度总体呈上升态势.O₃日变化呈"单峰型"，最大值出现在13：00左右，且峰值逐年增加，污染持续时间变长，最小值出现在早晨7：00.城区O₃"周末效应"逐渐减弱.基于KZ过滤器方法的数据分析结果表明，上海城区O₃-8 h长期变化主要受O₃-BF（O₃-8 h的基准组分）影响；O₃-SF（O₃-8 h的天气影响组分）在5—9月对O₃-8 h影响较大，其范围为-98.85~139.60 μg·m^-3.