含钒石煤烧渣的稳定化试验研究

研究了含钒石煤烧渣稳定化处理的一种有效方法。利用石灰为稳定剂与烧渣相混合进行稳定化处理,渣中的水溶态钒转化为钒酸钙沉淀而降低毒性。浸出试验表明,水中钒浓度〈5mg／h,并且具有长期的稳定性,无二次污染。     

电凝聚过程中消除电极钝化方法的研究进展

电凝聚法是一种对环境二次污染很小的废水处理技术,具有广阔的应用前景。但是,因其电化学过程中可溶性铝或铁阳极的钝化现象而限制了其高效低能耗应用。从电凝聚电极过程的分析入手,讨论了电极钝化的本质原因及消除电极钝化的措施,并介绍了笔者采用自行研制的交变脉冲电凝聚专用电源,彻底消除电极钝化方面的研究进展。     

基于视频识别的直接作业环节安全管控

概述了石化行业现场直接作业环节的安全管控现状,分析了现场管控过程中存在的问题。考虑现场安全管理和监督监控的实际需要,设计了石化行业直接作业现场智能化管控系统,并深入研究作业现场违章行为图像识别的关键技术。现场应用表明,系统充分体现了日常管理、实时监控、智能报警、统计分析等方面的便利性和有效性,各类违章行为图像识别准确率达到80%以上,具有一定的推广价值。     

基于风险梯度的化工企业事故风险定量评估

为了定量分析区域内重大危险源所构成的风险,为事故风险防控提供科学依据,基于风险场理论对某区域内2家化工企业进行风险分析,得出2家企业所对应的风险值计算公式,并生成2家企业所对应的风险等值面和风险等值线;引入最速下降法,利用负梯度搜寻风险的最快下降方向,得出事故的最优风险降低路径。研究结果表明:甲企业中接近1/2的区域为Ⅲ级风险区域,其余区域为Ⅱ级风险区域,乙企业中大部分区域为Ⅱ级风险区域,仅少部分区域属于Ⅲ级风险区域。相较而言,乙企业中5条最优风险降低路径里程更短,人员分配情况更为合理,更具安全优势;甲企业事故风险更大,更需要完善相关安全措施以免发生事故。     

过电流故障铝导线熔痕部位与组织特征关联性研究

为深入研究过电流故障铝导线熔痕部位与组织特征之间的关联关系,本文模拟2.5 mm²BLV铝导线通25～187.5 A电流时的发热、熔断和燃烧过程,研究过电流铝导线发热形变与熔痕形成的内在关联,根据各部位熔痕受热形成过程,分类识别典型组织特征。研究结果表明:随着电流值升高,铝导线先后出现线芯发热、绝缘热解、熔断拉弧、绝缘燃烧、重力折断等现象,发生熔断拉弧的临界电流值位于[71.5,73)A区间内;重力折断痕迹和导线本体组织受线芯发热和绝缘燃烧的共同影响,组织为粗大的块状晶,折断点为锯齿状寸断痕迹;熔断电弧熔痕为高温电弧作用于熔化金属后凝固形成,呈树枝状、纤维状铸态组织,分区分布,孔洞较少,表现为圆珠状、钝头状、尖头型、弯折状、牵拉状等5种典型形貌。通过建立熔痕部位与组织特征的关联,增加故障判断证据维度,为准确识别铝导线发生过电流故障及溯源起火过程提供数据支持。     

着床后引燃对电弧迸溅熔珠组织特征的影响

为探究迸溅熔珠着床后的热交换过程对其组织特征的影响,建立基于着床后高温迸溅熔珠的动态测温方法,从而揭示迸溅熔珠着床后引燃与否对其组织特征形成的影响规律。研究结果表明：引燃可燃物的熔珠受火焰热反馈和铜氧化放热的共同作用,着床后其温度出现反复波动,延长迸溅熔珠的冷却凝固时间,组织呈等轴状;无法引燃可燃物的熔珠在可测范围内,短暂升温后降温速率持续上升,组织更易呈现树枝状或胞状。研究结果可为准确认定电气故障电弧迸溅熔珠引发火灾提供技术支持。     

电力设备火灾危险性分析与防控技术

为研究电网及电力设备火灾危险性以及电力设备防火灭火技术,梳理归纳典型电力设备火灾机理与特性以及电力设备火灾风险、火灾相关的多灾种风险评估研究现状,介绍目前先进的电力设备火灾监控技术及典型电力设备防火灭火技术现状及发展趋势,并对电力设备火灾风险评估及防控未来发展趋势进行分析。研究结果表明：需进一步定量化和系统化进行风险分析与评估研究,智能化与全方位进行电力火灾监控,提高并完善灭火技术。研究结果可为电力设备火灾相关安全研究提供参考。     

土著致病菌及其胞外物在生物防治斑马贝中的作用

无脊椎动物斑马贝(Dreissena polymorpha) 的生物污损造成了巨大的经济损失,而应用从斑马贝体内分离出的土著菌株及其体外代谢产物对它进行生物防治是一种经济效益显著且对环境友好的方法.本文主要报导从斑马贝体内分离的土著菌株中筛选出致病菌并研究该细菌及其代谢产物对它的控制作用.在三十多种土著菌株中,中间气单胞菌( Aeromonas media),维罗纳气单胞菌(A. veronii),杀鲑气单胞菌杀鲑亚种(A. salmonicida subsp. salmonicida)和腐败希瓦氏菌(Shewanella putrefaciens)是幼体斑马贝的致命致病菌.当接种量为每只斑马贝107 个细菌时,接种中间气单胞菌、杀鲑气单胞菌杀鲑亚种和腐败希瓦氏菌的5 d 死亡率为100%,而维罗纳气单胞菌为65%.通过扫描电镜(SEM)发现,垂死的斑马贝肌肉组织被破坏并含有大量的细菌.4种细菌代谢产物的不同组分表现出对斑马贝不同的致死效果,在所研究的3种不同Mr组分中(Mr<5×103,5×103～10×103及>10×103),>10 ×103组分具有最高致死率.这些结果为控制贝类无脊椎动物的生物污损提供了新方法. 图4 参24     

A review of atmospheric mercury emissions,pollution and control in China

Mercury, as a global pollutant, has significant impacts on the environment and human health. The current state of atmospheric mercury emissions, pollution and control in China is comprehensively reviewed in this paper. With about 500-800 t of anthropogenic mercury emissions, China contributes 25%-40% to the global mercury emissions. The dominant mercury emission sources in China are coal combustion, non-ferrous metal smelting, cement production and iron and steel production. The mercury emissions from natural sources in China are equivalent to the anthropogenic mercury emissions. The atmospheric mercury concentration in China is about 2-10 times the background level of North Hemisphere. The mercury deposition fluxes in remote areas in China are usually in the range of 10-50μg·m^-2·yr^-1. To reduce mercury emissions, legislations have been enacted for power plants, non-ferrous metal smelters and waste incinerators. Currently mercury contented in the flue gas is mainly removed through existing air pollution control devices for sulfur dioxide, nitrogen oxides, and particles. Dedicated mercury control technologies are required in the future to further mitigate the mercury emissions in China.     

A red water occurrence in drinking water distribution systems caused by changes in water source in Beijing,China: mechanism analysis and control measures

A red water phenomenon occurred in several communities few days after the change of water source in Beijing, China in 2008. In this study, the origin of this problem, the mechanism of iron release and various control measures were investigated. The results indicated that a significant increase in sulphate concentration as a result of the new water source was the cause of the red water phenomenon. The mechanism of iron release was found that the high-concentration sulphate in the new water source disrupted the stable shell of scale on the inner pipe and led to the release of iron compounds. Experiments showed that the iron release rate in the new source water within pipe section was over 11-fold higher than that occurring within the local source water. The recovery of tap water quality lasted several months despite ameliora- tive measures being implemented, including adding phosphate, reducing the overall proportion of the new water source, elevating the pH and alkalinity, and utilizing free chlorine as a disinfectant instead of chloramine. Adding phosphate was more effective and more practical than the other measures. The iron release rate was decreased after the addition of 1.5 mg. L-1 orthophosphate- P, tripolyphosphate-P and hexametaphosphate-P by 68%, 83% and 87%, respectively. Elevating the pH and alkalinity also reduced the iron release rate by 50%. However, the iron release rate did not decreased after replacing chloramine by 0.5-0.8 mg. L-1 of free chlorine as disinfectant.