750kVGIS隔离开关用绝缘拉杆炸裂原因分析

盆式绝缘子、绝缘拉杆、支柱绝缘子等绝缘件作为GIS设备内部重要的绝缘、传动部件,故障率仅次于异物放电。通过绝缘拉杆运动特性分析、X射线成像检测、异物分析、微观分析、电场仿真分析等方法,对一起750 kV GIS 设备隔离开关交接试验过程击穿炸裂进行分析。针对分析结果给出了隔离开关的故障原因为连接机构侧的绝缘管粘接面加工操作不当造成了绝缘管层间疏松,导致粘接面存在气隙缺陷,缺陷逐渐延伸扩展,最终诱发绝缘拉杆层间连续放电通道。     

基于GOCI数据的太湖叶绿素a浓度反演和蓝藻水华遥感监测

太湖蓝藻水华是广为关注的环境问题,迫切需要实现蓝藻水华的动态监测。利用静止轨道海洋水色遥感器(GOCI)遥感数据构建了太湖叶绿素a反演的三波段模型,使用归一化植被覆盖指数(NDVI)进行蓝藻水华监测,并进行了富营养化评价。结果表明:(1)三波段模型优于波段比值模型,可以用于GOCI遥感数据反演太湖叶绿素a浓度。(2)2019年6月3日太湖叶绿素a大致呈湖心和西部浓度低,北部和西南沿岸浓度高的空间分布;从10:15至15:15,叶绿素a浓度先升高后降低。(3)竺山湖和椒山周边水域水华聚集情况较为严重,是当天重度水华的主要发生区域;水华的时间变化规律同叶绿素a浓度变化规律一致。(4)对2019年4月和6月的GOCI遥感数据进行富营养化评价发现,太湖富营养化水平总体呈西部高东部低、北部高南部低、边缘高中间低的趋势;6月较4月富营养化水平明显加剧。     

不同水力条件下圆柱桥墩局部冲刷试验研究∗

桥墩冲刷是导致桥梁水毁的主要原因,研究不同水力条件下局部冲刷对桥梁的影响具有重要意义。通过开展不同流速和水深下圆柱桥墩模型冲刷试验,研究了圆柱桥墩周围泥沙的局部冲刷发展规律,特别是流速和水深对桥墩局部冲刷的影响。试验研究表明:随着时间的发展,最大冲刷深度与冲刷坑范围在前期急剧发展,随后发展逐渐缓慢,直到冲刷处于近似平衡阶段。最大冲刷深度最开始出现在墩前侧方,随后始终出现在墩正前方附近,最小冲刷深度出现在墩的正后方附近,墩后的冲刷深度不足墩前深度的50%。流速和水深是影响桥墩的局部冲刷的关键因素,最大冲刷深度和冲刷坑的范围随着流速和水深增大而增大,相比于水深,冲刷深度和冲刷坑范围受流速的影响较大。     

一起鸟粪闪络引起220kV引流跳线与地线短接故障分析

对某220 kV输电线路跳闸故障进行分析,根据故障监测信息、故障时段故障区域的天气、现场环境等综合判断故障原因为鸟粪闪络,而造成鸟粪闪络的主要原因为跳线角钢未用绝缘护套包覆,鸟类夜间栖息在架空地线防振锤处排便,鸟粪在湿度80%RH、微风条件下降落,短接跳线角钢端头和地线防振锤间电气间隙而引起闪络放电。对绝缘护套的防鸟害效果进行仿真分析,得出了不同电压等级线路绝缘护套的最佳厚度,提出了防范类似鸟害故障的措施。     

碘量法测定水中溶解氧有关问题的探讨及改进

碘量法测定溶解氧时,采用NH3·H2O—KI代替NaOH(KOH)—KI固定溶解氧,用H2SO4—H3PO(41+1)混合酸代替H2SO4溶解沉淀,使沉淀沉降速度加快,分界线明显,沉淀溶解也更完全。同时做样品空白实验,校正了氧化还原性物质产生的干扰,对废水有明显的抗干扰能力。通过对蒸馏水、自来水、池塘水、废水进行溶解氧测定,结果均非常满意。     

新型涂料在弹药储运环境防护中的运用研究

在分析了弹药储运过程中恶劣的电磁环境基础上,结合目前我军弹药用涂料的现状,探索了利用膨胀石墨蠕虫作为填料,以聚氨酯清漆作为粘结剂的新型涂料的防静电性能,分析了膨胀石墨蠕虫的膨胀体积、填料含量、涂层厚度与电阻率的关系,并论述了新型弹药用涂料的应用前景。     

城市餐厨垃圾处置闭路循环体系的构建探讨--以上海市为例

随着我国城市社会经济的发展,城市餐厨垃圾的产生量持续增长,其安全回收和处置日益引起公众和社会的关注。以上海市为例,分析了上海城市餐厨垃圾产生以及回收处置的现状,探讨了城市餐厨垃圾处置闭路循环体系的建立,为国内其他城市餐厨垃圾的管理提供参考。     

Determination of Frequency for Remeasuring Ground and Vegetation Cover Factor Needed for Soil Erosion Modeling

Determining a remeasurement frequency of variables over time is required in monitoring environmental systems. This article demonstrates methods based on regression modeling and spatio-temporal variability to determine the time interval to remeasure the ground and vegetation cover factor on permanent plots for monitoring a soil erosion system. The spatio-temporal variability methods include use of historical data to predict semivariograms, modeling average temporal variability, and temporal interpolation by two-step kriging. The results show that for the cover factor, the relative errors of the prediction increase with an increased length of time interval between remeasurements when using the regression and semivariogram models. Given precision or accuracy requirements, appropriate time intervals can be determined. However, the remeasurement frequency also varies depending on the prediction interval time. As an alternative method, the range parameter of a semivariogram model can be used to quantify average temporal variability that approximates the maximum time interval between remeasurements. This method is simpler than regression and semivariogram modeling, but it requires a long-term dataset based on permanent plots. In addition, the temporal interpolation by two-step kriging is also used to determine the time interval. This method is applicable when remeasurements in time are not sufficient. If spatial and temporal remeasurements are sufficient, it can be expanded and applied to design spatial and temporal sampling simultaneously.     

Stream buffer effectiveness in an agriculturally influenced area, southwestern Georgia: responses of water quality, macroinvertebrates, and amphibians

To determine useful metrics for assessing stream water quality in the Southeastern Coastal Plain, we examined differences among two buffered and three unbuffered streams in an agricultural landscape in southwestern Georgia. Potential indicators included amphibian diversity and abundance, aquatic macroinvertebrate populations, riparian vegetative structure, water quality, and stream physical parameters. Variability among sites and treatments (buffered vs. unbuffered) existed, with sites in the same treatment as most similar, and disturbances from a nearby eroding gully strongly affecting one unbuffered site. Of the invertebrate metrics examined, percentages of clingers, Ephemeroptera-Plecoptera-Trichoptera (EPT), Elmidae (Coleoptera), Crustacea (Decapoda and Amphipoda), and dipterans were found to be possible indicators of stream health for perennial streams within this region. Overall, buffered sites showed higher percentages of sensitive invertebrate groups and showed lower and more stable concentrations of nitrate N, suspended solids, and fecal coliforms (FCs). Percent canopy cover was similar among sites; however, riparian vegetative coverage and percent leaf litter were greatest at buffered sites. No differences in amphibian abundance, presence, and absence within the riparian area were apparent between sites; however, instream larval salamanders were more abundant at buffered streams. In this study, stream buffers appeared to decrease nutrient and sediment loads to adjacent streams, enhancing overall water quality. Selected benthic macroinvertebrate metrics and amphibian abundance also appeared sensitive to agricultural influences. Amphibians show potential as indicator candidates, however further information is needed on their responses and tolerances to disturbances from the microhabitat to landscape levels.