单兵用主动式听力保护技术研究现状分析

战场噪声是造成单兵听力损伤的重要原因,通常要求单兵处于大于85dBA的噪声环境中需佩戴听力保护装置。听力保护装置通常包括耳罩式和耳塞式。新型单兵用耳塞式听力保护装置具有听力保护、环境声音的监听、持续及脉冲噪声抑制、通信接入等多种功能。     

Sorption of phthalate acid esters on black carbon from different sources

Black carbon (BC) is known as a strong sorbent for the sorption of planar hydrophobic organic compounds (HOCs), but there is very little information about the sorption of nonplanar HOCs on BC. In this study, the sorption of di-(2-ethyl-hexyl) phthalate (DEHP), one kind of nonplanar phthalate acid ester (PAE), by environmental BC collected from river sediments and pure BC (char-wood, char-stalk and soot-ash) was investigated. Strong and nonlinear sorption was observed for the sorption of DEHP on both pure BC and environmental BC with the Freundlich exponent ranging from 0.55 to 0.75 except for soot-ash, and the measured K(BC) (BC-water partition coefficient) of DEHP was about one order of magnitude higher than its organic carbon-water partition coefficient. There was a significant difference in sorption capacity among the environmental and pure BC. The presence of di-methyl phthalate (DMP) could significantly decrease the sorption of DEHP on BC, especially for environmental BC. In addition, the contribution of BC to the total sorption of DEHP on original river sediments was more than 50% when the equilibrium concentration of DEHP was less than 10 μg L(-1). This study indicated that ortho-substituted nonplanar PAEs could also be strongly sorbed by BC, and the difference in sorption among the BC samples revealed that it is important to take the source of BC into account when assessing its effects on the fate of HOCs in aquatic environment.     

1780-1819年华北平原水旱灾害社会响应方式的转变

历史时期水旱灾害的社会响应典型案例重建是气候变化影响与适应研究的重要方向。选取1780-1819年间华北平原发生的4次典型水旱灾害(1785、1792、1813年旱灾及1801年水灾),基于清代档案资料和历史气候重建结果提取代用指标,对其灾情严重程度、政府救灾力度和灾民行为进行了量化描述和对比分析,发现:①4次灾害中赈济密度(赈灾物资数/成灾州县数)逐次下降,1813年旱灾中降至不足1785年旱灾的1/6,政府救灾力度遭到严重削弱;②灾民行为日益失控,从1792年旱灾和1801年水灾中的大规模跨区域迁徙,发展到1813年旱灾中大量加入盗匪和起义军,走向暴力。这一转变的发生,是在自然(气候突变、灾害增多)、社会(政府财政危机、人地矛盾激化)不利背景之下,政府与灾民的互动关系日趋消极的结果。     

我国中东部不同地区冬季颗粒物垂直分布的车载移动观测

利用中山大学环境气象综合观测车（载有3D可视型激光雷达、多普勒风廓线激光雷达、转动拉曼温廓线激光雷达）于2018年冬季在全国范围内（厦门-北京）的走航观测资料,对我国中东部不同地区和城市的边界层结构以及颗粒物分布特征进行了研究.结果表明：(1)在从南向北走航的过程中,边界层内各个高度的温度以及边界层高度呈下降趋势.(2)不同高度发生颗粒物污染的气象成因有所差别,其中1000 m高度左右发生颗粒物污染的主要成因是较高的水平风速将周围地区的颗粒物输送过来而导致;500 m及近地面附近发生颗粒物污染主要是由水平风速较小导致局地来源的颗粒物堆积以及上游地区颗粒物的输送两者共同作用.(3)逆温结构和上升气流会导致颗粒物在边界层顶堆积,而下沉气流使得颗粒物由在某一高度堆积扩散至整层均匀分布.     

新烟碱类农药呋虫胺对映体选择性研究进展

农业生产中,呋虫胺以外消旋体的形式销售和使用,在进入生态环境后出现对映体选择性降解、吸收、代谢、排泄等.不区分对映体间差异的传统风险评估给呋虫胺的合理使用与生态安全带来了诸多隐患.研究指出S-呋虫胺既是高毒体也是高活体,其生态毒性为R-呋虫胺的13.9~145.9倍,但R-呋虫胺也表现出较高的杀虫活性,且作物中优先降解,开发高比例的R体农药有利于维持杀虫活性的同时降低对非靶生物和生态环境的负效应.本文旨在综述呋虫胺对映体选择性生物活性、生态毒性及环境行为研究进展,为其科学难题的解决提供新思路,也为其科学有效管理提供理论依据.     

城市空气质量达标规划的逻辑框架

针对环境空气质量达标规划目前没有明确规划编制的基本要求和主要内容之间的关联原则、未将长期规划方案落实到日常管理方案、过于重视长期空气质量目标与减排情景方案而对污染物减排方案重视不足、未将规划的成本效益分析作为主要方案设计依据等逻辑不清的问题,从人群健康的角度出发,构建达标规划的逻辑框架：提出空气质量目标和人群健康目标相一致的目标体系;设计与空气质量目标一致的污染物减排方案,通过成本效益或成本有效性分析明确优先序,按照重污染日（周）、重污染月、采暖期等优先序实施区域内污染物排放量的绝对减排,并落实到排污许可证中;实施空气质量“日”管理,根据预测模型对未来重污染天气进行污染源排放管理,并对污染源减排方案实施持续动态评估和调整.     

基于PMF模型解析典型化工园区VOCs污染来源应用研究

选取某小型化工园区为研究对象,在不同日期进行样品采集并使用气相色谱-质谱联用仪(GC-MS)定性定量分析,评估该区域VOCs污染水平及特征,同时研究P MF模型解析小尺度区域VOCs污染来源的可行性.结果表明,该研究区域VOCs浓度明显高于城市环境空气及其他化工园区,存在较重污染;该区域VOCs的主要成分为丙烯、苯、甲苯、萘、间-乙基甲苯、丙酮、丙烷、1,2,4-三甲苯、异丁烷等物质,各排放源污染特征显著,差异性明显;使用PMF模型对观测期间VOCs源解析,共获得4个因子,各因子与该区域不同排放源工艺及污染特征能够高度对应,并依此计算了各点位VOCs污染来源,结果与污染物扩散规律相符,PMF模型应用于小尺度污染物溯源分析具有可行性,能够很好地解析VOCs污染来源.     

局放检测技术在高压开关柜绝缘缺陷诊断与定位中的应用

针对石化企业电气设备绝缘状态检测现状,采用特高频检测、高频电流检测、超声波检测等常用局部放电检测方法,对某石化企业220 kV变电站35 kV开关柜局部放电检测,分析局部放电检测数据和图谱特征,综合运用高频电流检测和特高频检测实现绝缘缺陷类型的准确识别和故障的精确定位,为企业电气设备状态检修及维护提供了关键数据支持。     

油田井口加热炉烟尘排放超标原因分析及治理方法

针对井口加热炉燃用套管气出现的烟尘排放超标问题,从燃烧方式及燃料组成方面分析发现,加热炉所采用的扩散式燃烧,火焰面燃料侧缺少氧气,燃料产生热分解生成炭黑颗粒;另外,套管气含有大量的重碳烷烃,其稳定性差、分解温度低,加剧了热分解反应。因此,控制套管气质量和改变燃烧方式是治理烟尘排放超标的基本途径。但是井口加装轻烃回收装置,分离出套管气中的重碳烷烃,成本高不可行。最终,基于预混燃烧理论,设计了双调风预混燃烧装置,现场实施结果表明,不仅烟尘排放降低了87.8%,而且NOx排放降低了58.6%、热效率提升了8.2%。实践证明,预混燃烧是治理井口加热炉烟尘排放超标的有效方法。     

Effect of environmental parameters on the degradability of polymer films in laboratory-scale composting reactors

Previous research in our laboratory reported a convenient laboratory-scale composting test method to study the weight loss of polymer films in aerobic thermophilic (53°C) reactors maintained at a 60% moisture content. The laboratory-scale compost reactors contained the following synthetic compost mixture (percentage on dry-weight basis): tree leaves (45.0), shredded paper (16.5), food (6.7), meat (5.8), cow manure (17.5), sawdust (1.9), aluminum and steel shavings (2.4), glass beads (1.3), urea (1.9), and a compost seed (1.0) which is designated Mix-1 in this work. To simplify the laboratory-scale compost weight loss test method and better understand how compost mixture compositions and environmental parameters affect the rate of plastic degradation, a systematic variation of the synthetic mixture composition as well as the moisture content was carried out. Cellulose acetate (CA) with a degree of substitution (DS) value of 1.7 and cellophane films were chosen as test polymer substrates for this work. The extent of CA DS-1.7 and cellophane weight loss as a function of the exposure time remained unchanged when the metal and glass components of the mixture were excluded in Mix-2. Further study showed that large variations in the mixture composition such as the replacement of tree leaves, food, meat, and sawdust with steam-exploded wood and alfalfa (forming Mix-C) could be made with little or no change in the time dependence of CA DS-1.7 film weight loss. In contrast, substituting tree leaves, food, meat, cow manure, and sawdust with steam-exploded wood in combination with either Rabbit Choice (Mix-D) or starch and urea (Mix-E) resulted in a significant time increase (from 7 to 12 days) for the complete disappearance of CA DS-1.7 films. Interestingly, in this work no direct correlation was observed between the C/N ratio (which ranged from 13.9 to 61.4) and the CA DS-1.7 film weight loss. Decreasing moisture contents of the compost Mix-2 from 60 and 50 and 40% resulted in dramatic changes in polymer degradation such that CA DS-1.7 showed an increase in the time period for a complete disappearance of polymer films from 6 to 16 and 30 days, respectively.Guest Editor: Dr. Graham Swift, Rohm & Haas.Paper presented at the Bio/Environmentally Degradable Polymer Society—Second National Meeting, August 19–21, 1993, Chicago, Illinois.