基于暂态零序电流法的站内电缆监测系统及验证试验

及时发现变电站内电力电缆的故障对保证变电站安全稳定运行具有重要意义。介绍了1种基于暂态零序电流法的站内电缆监测系统,对系统的监测原理和各部件参数要求进行了论述,并采用单相失压模拟试验和人工单相接地试验对电缆线路监测系统进行了验证。试验结果表明,该系统可以准确地采集电缆线路故障发生时的暂态零序电流,并能及时将故障报警信息上报运维人员,保证变电站安全稳定运行。     

2种防护涂层体系在湿热海洋环境下防护性能的劣化规律研究

目的 研究2种防护涂层体系在湿热海洋环境下自然暴露3 a的防护性能劣化规律。方法 确定试验件为钢–铝（钢）螺接连接件,试验地点为海南万宁,并按周期测得不同暴露时间下涂层A和涂层B的外观形貌、色差、光泽度、表面傅里叶红外光谱、电化学阻抗的相关数据。通过对比分析测试结果,判断2种涂层在不同暴露时间下的劣化程度,并最终得到其劣化规律。结果 涂层A自然暴露1 a老化严重,紧固件区域涂层剥落,平板区域失光率约为75%,阻抗模量降低5个数量级,色差ΔE~*为5（轻微变色）,涂层有机基团老化降解严重。涂层B自然暴露2 a,老化较严重,紧固件区域涂层剥落、生锈,平板失光率约为20%,阻抗模量降低2个数量级,色差ΔE~*为11（严重变色）,涂层有机基团轻微老化降解。结论 对于螺钉连接结构,连接区域不仅更容易被腐蚀,而且增加了附近平板区域的不一致性。涂层体系B的保护能力优于涂层体系A,涂层体系B的有效保护时间约为2 a,而涂层体系A则不到1 a。     

矿物棉填料孔隙率对生物滴滤池水处理效果的影响

针对生物滴滤池因接触时间短而导致出水不达标的问题,采用3种容重(80、100、120 kg·m-3)的矿物棉作为滤池填料,考察了填料孔隙率对保水性的影响,分析了不同容重填料的生物滴滤池去除污染物的效能,探究了填料孔隙率对微生物群落特征的影响。结果表明,矿物棉载体的吸水、保水性能随其孔隙率增加呈现先增加后减小的趋势;孔隙率较小的矿物棉载体在稳定运行后对COD、NH4+-N有更好的去除效果,平均去除率分别可达99%和72%,且具有一定的抗冲击负荷能力。高通量测序结果显示,随着矿物棉载体孔隙率的减小,微生物群落物种丰富度增加,而其多样性减少。比较而言,当容重为100 kg·m-3时,矿物棉的吸、保水性高,微生物种群结构适宜,出水水质可达一级A标准,且具有一定的抗冲击负荷能力。     

燃煤电厂排放颗粒物中重金属形态的研究

本文分析用模拟酸雨浸提和Ｔｅｓｓｉｅｒ形态分离法，对燃煤电厂排放颗粒物中重金属形态进行了研究。结果表明，痕量金属绝大部分以稳定态存在，微米级飞灰中有较大活性的形态高于灰渣，煤燃烧高温条件使颗粒物中活性较大的形态含量减小。     

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.     

生物处理过程中活性污泥对氯代芳香化合物吸附性能的研究

本文研究了邻二氯苯 和邻氯酚生物处理过程中在活性污泥上的吸附特性及影响因素。通过测定等温吸附曲线,表明这两种有机化合物在活性污泥上的吸附符合线性吸附等温式：属于在疏水键力作用下的表面物理吸附,对难溶于水的邻二氯苯具有较强的吸附能力。     

三江平原不同水位梯度湿地地上生物量动态特征

水分条件变化直接影响湿地植物群落的分布及其生产量,为了阐明不同水分条件湿地初级生产力的形成规律,揭示水文格局对湿地生态系统物质生产过程的调控机理,采用收获法研究了三江平原不同水位梯度上的小叶章(Calamagrostics angustifolia)、乌拉苔草(Carex meyeriana)和毛苔草(Carex lasiocarpa)湿地地上生物量的结构动态及其增长速率,结果表明:3类湿地地上及其各器官生物量均呈单峰型变化,小叶章湿地和乌拉苔草湿地地上生物量的峰值出现的时间早于毛苔草湿地,而且小叶章湿地和乌拉苔草湿地各季节地上生物量均大于毛苔草湿地.茎对小叶章湿地地上生物量的平均贡献率与毛苔草湿地相近,均大于乌拉苔草湿地;叶对小叶章湿地地上生物量的平均贡献率与毛苔草湿地相近,均小于乌拉苔草湿地.3类湿地地上生物量的绝对增长率和相对增长率的变化趋势基本相同,但不同阶段绝对增长率和相对增长率值的大小存在差异.3类湿地地上生物量及各组分生物量的季节动态变化均符合抛物线模型,并且各模型拟合精度均较高,R2基本都在0.92以上.     

两种改性剂对多氯联苯污染土壤协同热脱附影响研究

采用热脱附技术处理多氯联苯污染土壤已经成为了一种主要的场地修复方式。为提高热脱附效率,降低能耗,以典型电力电容器污染土壤为对象,采用2种改性剂(零价纳米铁和氢氧化钠)研究协同热脱附下多氯联苯的去除效率、分布特性及毒性当量。结果表明纳米铁和NaOH存在的条件下,有效提高了多氯联苯和毒性当量的去除效率,在较低温度下尤其显著,因此添加改性剂能够有效地促进热脱附过程。纳米铁的协同热脱附机理为显著强化了热脱附过程的传质传热,同时伴有一定的脱氯降解。NaOH的添加在较低温度下实现了较强的脱氯降解作用,加氢脱氯机理可用来解释协同热脱附过程中多氯联苯的脱氯反应过程。上述研究结果为多氯联苯污染土壤的场地修复提供理论基础。     

Control concept and countermeasures for shallow lakes’ eutrophication in China

Research on lake eutrophication in China began in the early 1970s, and many lakes in China are now known to be in meso-eutrophic status. Lake eutrophication has been showing a rapidly increasing trend since 2000. Investigations show that the main reasons for lake eutrophication include a fragile lake background environment, excessive nutrient loading into lakes, excessive human activities, ecological degeneration, weak environmental protection awareness, and lax lake management. Major mechanisms resulting from lake eutrophication include nutrient recycling imbalance, major changes in water chemistry (pH, oxygen, and carbon), lake ecosystem imbalance, and algal prevalence in lakes. Some concepts for controlling eutrophication should be persistently proposed, including lake catchment control, combination of pollutant source control with ecological restoration, protection of three important aspects (terrestrial ecology, lake coast zone, and submerged plant), and combination of lake management with regulation. Measures to control lake eutrophication should include pollution source control (i.e., optimize industrial structural adjustments in the lake catchment, reduce nitrogen and phosphorus emission amounts, and control endogenous pollution) and lake ecological restoration (i.e. establish a zone-lake buffer region and lakeside zone, protect regional vegetation, utilize hydrophytes in renovation technology); countermeasures for lake management should include implementing water quality management, identifying environmental and lake water goals, legislating and formulating laws and regulations to protect lakes, strengthening publicity and the education of people, increasing public awareness through participation in systems and mechanic innovations, establishing lake region management institutions, and ensuring implementation of governance and management measures.