汞的形态分析进展

汞的测定方法由总汞测定深入到汞的形态分析，综述近几年来汞的形态分析方法的发展，包括原子光谱法、气相色谱法、液相色谱法，毛细管电泳法和电化学分析法。     

湘中涟源煤盆测水组煤动力变质作用的特征及其成因探讨

从煤变质程度、煤变质特征、煤变质带展布、煤的物理性质和结构构造、煤化学结构等方面．论述了湘中涟源煤盆早石炭世测水组煤动力变质作用的特征，并对其成因进行了探讨。     

盐间非砂岩低渗透油藏中原油运移动力学分析

独特的江汉盆地潜江凹陷潜江组盐间非砂岩油藏生储同层 ,盐岩封盖条件极佳 ,但储集层渗透能力极低 ,油气运移条件差。目前的众多证据表明 ,就是在渗透能力如此低下的盐间层中 ,非断裂区的原油也顺层发生了一定规模的运移。在压实作用、流体热增压、有机质生烃生气增压以及毛细管压差等应力作用下 ,盐间原油得以从烃源岩层中排除 ,并在低渗透的盐间层运移主干道中顺层侧向 (或断裂区垂向穿层 )从生烃次洼向构造高部位等低势区聚集。从动力学的角度证明了盐间非砂岩低渗透油藏中原油顺层运移的可能性 ,并指出了盐间石油的运移方向和有利聚集区。     

挥发性卤代烃的天然来源及其生成机制

天然产生的挥发性卤代烃(VHC)，对大气中VHC的源汇平衡有显著影响。不同生态系统中VHC的天然生成机制存在很大差异，有许多天然过程还不为人们所了解。该文对海洋，陆地等生态系统中VHC的天然来源及其产生机制进行了较全面的综述。     

Cause of PM2.5 pollution during the 2016-2017 heating season in Beijing, Tianjin, and Langfang, China

To investigate the cause of fine particulate matter (particles with an aerodynamic diameter less than 2.5 µm, PM_2.5) pollution in the heating season in the North China Plain (specifically Beijing, Tianjin, and Langfang), water-soluble ions and carbonaceous components in PM_2.5 were simultaneously measured by online instruments with 1-hr resolution, from November 15, 2016 to March 15, 2017. The results showed extreme severity of PM_2.5 pollution on a regional scale. Secondary inorganic ions (SNA, i.e., NO₃^?+SO₄²+ NH₄⁺) dominated the water-soluble ions, accounting for 30%-40% of PM_2.5, while the total carbon (TC, i.e., OC + EC) contributed to 26.5%-30.1% of PM_2.5 in the three cities. SNA were mainly responsible for the increasing PM_2.5 pollution compared with organic matter (OM). NO₃^? was the most abundant species among water-soluble ions, but SO₄^2- played a much more important role in driving the elevated PM_2.5 concentrations. The relative humidity (RH) and its precursor SO₂ were the key factors affecting the formation of sulfate. Homogeneous reactions dominated the formation of nitrate which was mainly limited by HNO₃ in ammonia-rich conditions. Secondary formation and regional transport from the heavily polluted region promoted the growth of PM_2.5 concentrations in the formation stage of PM_2.5 pollution in Beijing and Langfang. Regional transport or local emissions, along with secondary formation, made great contributions to the PM_2.5 pollution in the evolution stage of PM_2.5 pollution in Beijing and Langfang. The favourable meteorological conditions and regional transport from a relatively clean region both favored the diffusion of pollutants in all three cities.     

南通市酸雨污染与成因分析

采用大量酸雨实测数据,全面系统地研究分析南通市酸雨污染状况,从区域性影响、局地污染影响和大气颗粒物缓冲能力等方面研究南通市酸雨污染的成因,为南通市环境综合决策和酸雨污染控制提供科学依据。     

湖南省酸性降水的研究

根据1993年春季在京广线湖南段区域的观测结果,对酸性降水的污染状况、特征、成因及其来源进行了分析和探讨。结果表明:湖南地区春季降雨是“严重污染的硫酸型酸雨";形成的机制与华南地区基本相同,污染物浓度是局地源贡献和外地源输送的叠加。      

城市面源污染形成过程及其排放特征研究进展

随着城市的迅速发展,城市面源污染日益成为影响城市水体水质的重要因素。本文按照地表累积—降水—径流冲刷—输送这一城市面源污染的形成过程对次降雨径流平均浓度、初始冲刷效益等污染特征进行了研究,分析了不同下垫面及不同功能区的污染特性。     

可吸入颗粒物研究现状及发展综述

可吸入颗粒物严重影响空气质量和人体健康。人类对可吸入颗粒物的研究已经取得了相当多的成果,对其来源、组分及形成等都有了一定的认识。本文详细的综述了这部分内容,并对可吸入颗粒物的采样、分离和分析方法都做了介绍。更深层的认识可吸入颗粒物的生成机理和脱除手段是以后努力研究的方向。     

Ozone and secondary organic aerosol formation potential from anthropogenic volatile organic compounds emissions in China

Volatile organic compounds (VOCs) are major precursors for ozone and secondary organic aerosol (SOA), both of which greatly harm human health and significantly affect the Earth''s climate. We simultaneously estimated ozone and SOA formation from anthropogenic VOCs emissions in China by employing photochemical ozone creation potential (POCP) values and SOA yields. We gave special attention to large molecular species and adopted the SOA yield curves from latest smog chamber experiments. The estimation shows that alkylbenzenes are greatest contributors to both ozone and SOA formation (36.0% and 51.6%, respectively), while toluene and xylenes are largest contributing individual VOCs. Industry solvent use, industry process and domestic combustion are three sectors with the largest contributions to both ozone (24.7%, 23.0% and 17.8%, respectively) and SOA (22.9%, 34.6% and 19.6%, respectively) formation. In terms of the formation potential per unit VOCs emission, ozone is sensitive to open biomass burning, transportation, and domestic solvent use, and SOA is sensitive to industry process, domestic solvent use, and domestic combustion. Biomass stoves, paint application in industrial protection and buildings, adhesives application are key individual sources to ozone and SOA formation, whether measured by total contribution or contribution per unit VOCs emission. The results imply that current VOCs control policies should be extended to cover most important industrial sources, and the control measures for biomass stoves should be tightened. Finally, discrepant VOCs control policies should be implemented in different regions based on their ozone/aerosol concentration levels and dominant emission sources for ozone and SOA formation potential.