电器实验室安全和环境监控措施探讨

电器实验室在对电器产品实施安全性能检测的过程中,实验室本身存在着安全和环境污染问题。如何对实验室的日电器实验室在对电器产品实施安全性能检测的过程中,实验室本身存在着安全和环境污染问题。如何对实验室的日常运作进行安全和环境的有效监控,对于保护实验室仪器设备和生命财产安全,以及试验人员的健康,具有重要的意义。 电器实验室安全和环境问题涉及但不限于防火、防烫伤、防暴、防触电、防机械伤害、防淋水、防盗、限制区域的禁入、仪器设备的保护、试验负荷控制、环境温度、湿度、电网电压、谐波畸变、噪音、有毒有害气体、电磁渡污染等诸多方面。本文针对电器实验室存在的一些主要安全和环境问题,从经济和技术可行性方面研究有效解决方法,并提出一种利用现代科技实现远程综合监控的方案。     

ASE萃取-GPC净化-HPLC法测定土壤中阿特拉津

以二氯甲烷-丙酮（体积比1∶1）为混合溶剂,用加速溶剂萃取仪萃取土壤样品中的阿特拉津,提取液通过凝胶渗透色谱净化,用高效液相色谱仪在220 nm波长下测定,试验表明,在0．05 mg/L～5．00 mg/L范围内线性良好。方法检出限为0．22μg/kg,对空白土壤进行加标回收,平行测定6次,平均回收率为88．2％～102％,RSD为4．5％～7．6％,符合农药残留分析的要求。     

Pilot scale evaluation of the BABIU process – Upgrading of landfill gas or biogas with the use of MSWI bottom ash

Biogas or landfill gas can be converted to a high-grade gas rich in methane with the use of municipal solid waste incineration bottom ash as a reactant for fixation of CO₂ and H₂S. In order to verify results previously obtained at a laboratory scale with 65–90 kg of bottom ash (BA), several test runs were performed at a pilot scale, using 500–1000 kg of bottom ash and up to 9.2 N m³/h real landfill gas from a landfill in the Tuscany region (Italy). The input flow rate was altered. The best process performance was observed at a input flow rate of 3.7 N m³/(h t_BA). At this flow rate, the removal efficiencies for H₂S were approximately 99.5–99%.     

结构振动疲劳加速试验技术研究

目的提出一种用于评估随机振动环境下工程结构长期耐久性和疲劳可靠性的加速试验技术。方法通过开展一系列高斯和非高斯振动疲劳对比试验,系统研究影响结构振动疲劳寿命的各种因素,包括随机振动激励的均方根值、功率谱密度、带宽和峭度值等。结果非高斯随机振动激励的带宽和峭度值对结构振动疲劳寿命也有明显影响。结论当结构振动激励呈现明显的非高斯特征时,设计随机振动疲劳加速试验方案必须综合考虑振动激励的带宽和峭度值。     

Accelerated degradation of carbofuran in standing water from carbofuran‐retreated Azolla plots

Abstract

Carbofuran (2, 3‐dihydro‐2, 2‐dimethyl‐7‐benzofuranyl N‐methylcarbamate) was mixed with standing water from six flooded Azolla (a fern harboring a nitrogen fixing alga, Anabaena azollae) plots that had been regularly treated with carbofuran before. The insecticide completely disappeared in 5 to 10 days when mixed with water from three of the six plots. The enrichment culture, prepared by further additions of carbofuran to the standing water from an Azolla plot, degraded bendiocarb (2, 2‐dimethyl‐l, 3‐benzidioxol‐4‐yl‐N‐methylcarbamate), carbofuran and carbosulfan [2,3‐dihydro‐2,2‐dimethyl‐7‐benzofuranyl (di‐n‐butyl‐aoinosulfenyl) methyl‐carbamate ] in that order. Enrichment culture, upon sterilization by autoclavlng, lost its ability to degrade carbofuran. Evidently, accelerated degradation of carbofuran in standing water from retreated Azolla plots was mediated by microorganisms.     

室内装饰装修材料测试舱的研制与应用

介绍了测试舱的研制意义、测试舱构造和温度控制部分,以及空气交换、循环控制,空气净化装置和温度、湿度、流速显示装置等.通过实验,对测试舱的温度控制,空气净化系统检验,空气交换、循环的检验,释放甲醛平衡点的快速判断和测试舱的比对等运行技术指标进行了论证、优化.结果表明,简易的室内装饰装修材料测试舱对主要运行参数可以自动运行与控制,运行情况满足国家标准方法的技术指标要求,与同类商品化测试舱相比,误差在2%左右.     

利用温度,压力变化进行样品前处理的新方法

文章介绍了亚临界水萃取，全蒸发技术和加速溶剂萃取这３种与温度压力有关的样品前处理的原理，及应用实例；通过与经典的索氏萃取法和超声以法的比较，表明这３种方法符合目前处理无溶剂化的潮流，具有萃取效率高，应用广泛的特点。     

Compression Molding of Phenolic Resin and Corn-based DDGS Blends

With the rapid growth in the ethanol fuel industry in recent years, considerable research is being devoted to optimizing the use of processing coproducts, such as distillers dried grains with solubles (DDGS), in livestock diets. Because these residues contain high fiber levels, they may be amendable to incorporation into bio-based composites. Thus, the goal of this study was to demonstrate the viability of using corn-based DDGS as a biofiller with phenolic resin, in order to produce a novel biomaterial. DDGS was blended with phenolic resin at 0, 10, 25, 50, 75, and 90%, by weight, and then compression molded at 51 MPa (3.7 tons/in²) and 174 °C (345°F). Molded specimens were then tested for tensile strength. Tensile yield strengths ranged from 32 MPa (4,700 psi) to 7.6 MPa (1,100 psi), while the engineering strain ranged from 0.6% to 1.25%. Results indicate that DDGS concentrations between 25% and 50% retained sufficient mechanical strength and thus represent reasonable inclusion values. Additionally, data were similar to those from other studies that have investigated biofillers. Follow-up studies should quantify the effects of altering molding parameters, including molding pressure, temperature, and time, as well as pretreatment of the DDGS. Additionally, strength of the DDGS composites should be optimized through the use of coupling agents or other additives. Mention of a trade name, proprietary product, or specific equipment does not constitute a guarantee or warranty by the United States Department of Agriculture and does not imply approval of a product to the exclusion of others that may be suitable.     

材料以及产品的环境试验方法

本文主要分析了各环境因素及其引起的失效模式,介绍了环境试验方法以及环境试验设计过程中应当注意的问题等基础知识,还给出了一些常用的环境试验标准.     

不同方法对南方几种土壤阳离子交换性质的测定比较

分別采用1mol L~(-1) NH_4OAC淋洗法,0.1mol L~(-1)BaCl_2捕掳交换法,6.667×10~(-3)mol L~(-1)Co(NH_3)_6Cl_3提取法以及电荷测定法测定了南方几种不同性质的土壤的阳离子交换性质。结果表明,酸性土壤的阳离子交换量具有不定性,NH_4OAC法的结果很高,而其它方法的结果显著偏低,但方法间仍存在显著差异。不过,各法对微酸性、中性土壤的测定结果无显著差异。与NH_4OAC法相比,BaCl_2法得到较多的Ca,而Co法则交换出较少的K。各法的浸提液pH间虽存在差异,但彼此间有良好的统计相关性。Co法测定的CEC值与交换性阳离子总和较为吻合,其浸提液pH与pH_(KCl)、pH_(CaCl_2)有良好的线性关系。看来,不同方法对酸性土壤阳离子交换量的测定差异主要来自測定过程中介质pH条件及离子强度不同所浸出的交换性酸的多寡。本文认为,Co(NH_2)_6Cl_3法可以作为这些土壤阳离子交换性质测定的例行方法。