嗅觉实验配气方法的改进及影响因素研究

配制气体样品是异味测试及相关研究的基础工作,配气稳定性直接影响测试结果准确度。三点比较式臭袋法使用微量进样针量取并转移液体标准物质到3L无臭气袋的传统配气方法。对于异味阈值较小物质或样品浓度处于较低范围时,为了降低取样体积波动对配气精度和稳定性的影响。提出先将标准注入100mL玻璃注射器,充分挥发混匀后再转移部分气体到无臭气袋的两步式配气方法。结果表明,2种配气方法的准确度不存在显著差异,但两步式配气法的配气稳定性明显优于传统方法。此外,研究还发现,常见异味物质在被注人气袋后3min内便能完全挥发并混合均匀。除一些挥发性和吸附性极强的物质外,气袋内的异味物质气体浓度能在配好后20min内基本保持不变。     

超高斯（分布）随机振动HALT试验剖面建立要点解析

本文介绍了超高斯（分布）随机振动HALT技术,对超高斯（分布）随机振动HALT试验剖面的建立提出了方法和建议,主要包括试验顺序的选择、应力强度的确定、步进量级的选择、驻留时间确定和试验停止原则等五方面,并总结了现场试验的要求和注意事项。     

振动试验中常见问题的分析

振动试验是装备环境试验不可缺少的部分,本文分析了试验条件的制定、试验夹具的设计和试验样品安装等振动试验中比较重要的环节,提出了振动试验实施过程中常见的几个问题,并结合实际操作经验给出了解决方案。     

高低温试验能力验证常见不满意原因分析

测量审核和实验室间比对是能力验证计划的有效补充形式,是实验室或者检查机构用于实验室质量控制及申请CNAS认可的重要手段。本文随机抽取2010年～2012年低温试验测量审核与高温试验实验室间比对结果为不满意的报告各8份作为样本,进行原因分析,并给出技术建议,旨在让参加实验室在以后的相关试验中能规避常见问题,提高测试能力。     

基于GJB 150A-2009的高温试验方法研究

介绍了GJB 150换版后的基本信息,以图表形式给出了高温对装备的影响及比重。对GJB150A-2009中的高温试验方法及剪裁指南进行了研究,对高温试验应用要点进行了分析,并以某型号电子装备为例,建立了其寿命期剖面和寿命期环境剖面。     

土壤中重金属检测样品前处理技术现状分析

土壤中重金属检测样品前处理是一个复杂且关键的步骤,对最终分析结果有重要的影响。文章对目前主要采用湿法消解(盐酸-硝酸-高氯酸-氢氟酸、王水/王水回流、反王水)、干灰化法消解与微波消解技术及其现状进行介绍,指出其各自的优势与存在问题,为土壤中重金属检测样品前处理技术的进一步探索研究提供参考。     

Epiphytic lichen diversity in central European oak forests: Assessment of the effects of natural environmental factors and human influences

We investigated lichen diversity in temperate oak forests using standardized protocols. Forty-eight sites were sampled in the Czech Republic, Slovakia and Hungary. The effects of natural environmental predictors and human influences on lichen diversity (lichen diversity value, species richness) were analysed by means of correlation tests. We found that lichen diversity responded differently to environmental predictors between two regions with different human impact. In the industrial region, air pollution was the strongest factor. In the agricultural to highly forested regions, lichen diversity was strongly influenced by forest age and forest fragmentation. We found that several natural factors can in some cases obscure the effect of human influences. Thus, factors of naturality gradient must be considered (both statistically and interpretively) when studying human impact on lichen diversity.     

Variability of sediment-contact tests in freshwater sediments with low-level anthropogenic contamination - Determination of toxicity thresholds

Freshwater sediments with low levels of anthropogenic contamination and a broad range of geochemical properties were investigated using various sediment-contact tests in order to study the natural variability and to define toxicity thresholds for the various toxicity endpoints. Tests were performed with bacteria (Arthrobacter globiformis), yeast (Saccharomyces cerevisiae), nematodes (Caenorhabditis elegans), oligochaetes (Lumbriculus variegatus), higher plants (Myriophyllum aquaticum), and the eggs of zebrafish (Danio rerio). The variability in the response of some of the contact tests could be explained by particle size distribution and organic content. Only for two native sediments could a pollution effect not be excluded. Based on the minimal detectable difference (MDD) and the maximal tolerable inhibition (MTI), toxicity thresholds (% inhibition compared to the control) were derived for each toxicity parameter: >20% for plant growth and fish-egg survival, >25% for nematode growth and oligochaete reproduction, >50% for nematode reproduction and >60% for bacterial enzyme activity.     

一株氧化亚铁硫杆菌的筛选及生长条件研究

从广东省大宝山矿区尾矿中分离纯化得到一株嗜酸细菌,对其进行DNA提取和16S rRNA扩增后测序,将测序结果与国际基因数据库Genbank中已有相关菌株序列进行相似性比对后,发现该菌株与氧化亚铁硫杆菌(Acidithiobacil-lus ferrooxidans)Tf-49菌位于系统发育树的同一分支中,二者相似度高达99%以上,确定其为氧化亚铁硫杆菌并命名为DBS-8菌。另外,通过设计5因素4水平的正交实验,研究了接种量、培养温度、硫酸铵浓度、初始pH和初始亚铁浓度对该菌株生长状况的影响。结果表明适宜该菌株生长的最佳初始条件为:20%的接种量、3.0 g/L硫酸铵、9.0 g/L初始亚铁、pH=2.0和28℃培养,各初始条件对细菌生长影响的顺序为:pH初始亚铁浓度接种量温度硫酸铵浓度。     

The toxicity of composted sediments from Mediterranean ports evaluated by several bioassays

This work investigates the ecotoxicological evaluation of contaminated dredged sediments from French Mediterranean navy harbour (A), commercial port (B) and two composite specimens (C) and (D) coming from the mixture of A and B with other port sediments. The toxicity of elutriates from these sediments is estimated using embryo-toxicity test, Microtox® solid phase test, LuminoTox, phytotoxicity tests and genotoxicity test. Bioassay responses are not clearly correlated with chemical contamination in the whole sediment and vary as a function of tested organisms. The highest contaminated samples (A and C) are almost always more toxic than the less contaminated samples (B and D). Among composite sediments, the mixture effect with other sediments is not efficient to decrease toxicity in sample C, suggesting that other parameters influence toxicity level such as particle size or organic matter content. These parameters should be taken into consideration in order to improve the efficiency of the mixture process and produce composite sediments with low toxicity.