CuO对贵金属/CeO2/Al2O3催化剂的作用

制备含少量贵金属Ｐｔ、Ｐｄ的不同Ｃｕ和Ｃｅ摩尔含量比（０：１０,１：９,２：８）的催化剂,实验条件十加入ＣｕＯ可以提高Ｐｔ催化剂的二效活性;加入Ｃｕ：Ｃｅ＝２：８的ＣｕＯ降低了Ｐｄ催化剂的顾效性能,然而Ｃｕ：Ｃｅ＝１：９时可以改善Ｐｄ催化剂的三效催化性能。通过结构分析,认为ＣｕＯ的存在可以提高ｄ催化剂的比表面积,ＰｄＯ的分散度。     

废水处理中pH值计算机模糊控制系统的设计

酸碱中和是化工废水处理中的一个重要环节。本ｐＨ值控制系统采用ＰＩＤ控制和模糊控制并列转换形式,当系统的偏差较小时,采用ＰＩＤ法进行流程控制;而当系统的偏差较大时,采用计算机模糊控制。介绍ｐＨ值计算机模糊控制系统设计原理与模糊控制器的实现,包括模糊化处理、模糊规则库的建立、模糊计算和反模糊化处理。在废水处理工艺流程中采用该控制方法可获得高效、稳定的控制效果。     

农药对藻类的生态毒理学研究Ⅰ:毒性效应

随着现代农业的发展,世界范围内使用的农药品种越来越多,用量不断增加。农药对非靶生物的影响以及农药残留导致环境污染,造成生态系统结构和功能的破坏,早已受到了国内外的广泛关注。有关农药对生态系统中消费者类群毒性效应的研究较多。近年来,农药对于生态系统初级生产者－ 藻类的毒性及其生态毒理学的研究倍受重视。大力开展这方面的研究对于深入了解农药在生态系统中的迁移、转化及整体生态效应以及农药的生态风险评价无疑具有重要的理论意义和应用价值。本文综述了近年来国内外有关农药对单种藻类和藻类群落的毒性效应,影响毒性的环境因子。     

提高环评报告书质量加快浙江省环境影响评价有效性建设

影响环境影响评价(EIA)有效性的因素较多．如相应的政策法规、管理机制和技术的正确性等。文章从环评技术角度出发,以抽样选取的浙江省1997～2001年间完成的100本环评报告书(EIS)为统计对象．按建设项目环保审批6项原则为依据,从产业政策符合性、选址与总图布局合理性、清洁生产、达标排放、总量控制、区域环境质量可达性等方面进行分析．评估了浙江省EIA有效性,探讨了目前EIA中存在的问题及原冈,提出了一些提高EIS质量、加快浙江省EIA有效性建设的建议     

低浓度Pb2+、Cd2+对鲫鱼肝脏组织中 HSP70诱导的影响

以鲫鱼(Carassius auratus)作为实验对象,经过40 d Pb2+、Cd2+不同浓度的暴露后,运用SDS-PAGE和Western Blotting方法检测鱼肝脏组织内应激蛋白HSP70的诱导表达情况.结果表明,在实验浓度下,与对照组相比,Pb2+、Cd2+对鱼肝脏内HSP70有显著的诱导(P＜0.05),但在Cd2+浓度为0.2 mg/L有停止表达HSP70的现象,可能是由于浓度过高造成了组织病理损伤而破坏了诱导表达机制.实验还发现,在实验浓度低于国家渔业用水标准时,HSP70仍然表现为明显诱导(P＜0.05),充分说明运用分子生物学指标要比传统的环境检测指标敏感,具有对污染物早期预警的作用.     

壬基酚及其短链聚氧乙烯醚在污泥和土壤中的存在和降解

壬基酚聚氧乙烯醚(NPnEO)是广泛使用的表面活性剂．在污水处理厂中会降解为具有内分泌干扰效应的短链产物和最终产物壬基酚(NP)。剩余污泥是其进入环境的重要途径。介绍了NP和短链NPnEO在污泥中的存在情况、污泥处理过程对其存在的影响、以及这些物质随污泥处置过程进入土壤后的降解。     

船桥撞击力影响因素有限元仿真模拟分析∗

为了探究船桥碰撞时船撞力的影响因素,选取合适的船撞力为桥梁设计提供参考,采用动力分析软件 LS ? DYNA,结合沪通长江大桥、天生港专用航道桥以及厦漳大桥三座实桥,分别进行了不同船速、不同通航水位、不同基础形式和不同船型等因素对船撞力的影响分析研究。研究结果表明：船撞力峰值和船速正相关;中通行水位时, 船桥撞击动力响应最大;不同桥墩基础和不同船型对船撞力有较大影响。基于中国铁路规范和有限元计算结果, 考虑了船舶类型和基础类型对船撞力的影响,对船撞力计算公式提出改进方法,所得研究结果可为桥梁抗撞设计和研究提供参考。     

Influence of osmotic distillation on membrane absorption for the treatment of high strength ammonia wastewater

Osmotic distillation (OD) was found to be a coupled process in membrane absorption (MA) for the treatment of high strength ammonia wastewater. As a result, ammonia could not be concentrated in absorption solution(AS) as expected. The inhibition of the coupled OD in MA process was investigated as well as various factors affecting the inhibition. The results indicated that the coupled OD can be effectively inhibited by heating concentrated solution and cooling dilute solution. It was also found that experimental minimum inhibition temperature difference(MITD) between concentrated and dilute solutions was different when using polyvinylidene fluoride(PVDF) and polypropylene(PP) membranes respectively, which could be ascribed to material properties, such as OD and membrane distillation (MD) coefficients of the membranes. Experimental MITDs were found to be higher than theoretical MITDs which were calculated using a simplified method.     

Experimental study on pollutant movement in surf zone

The experiments on pollutant movement in surf zone were conducted on the two gentle beaches(with slope of 1:100 and 1:40, respectively), for diverse wave cases. The movement contours and direction of pollutants, under the action of regular and random waves with diverse wave amplitudes, were provided and studied in this paper. It was shown that, due to complicated hydrodynamics in surf zone, the pollutant movement state is quite complicated and different from that in pure current zone.     

Effects of traffic pollution on the genetic structure of Poa annua L. populations

The genetic composition of Poa annua L, populations with a series of traffic pollution was studied by starch electrophoresis. Five enzyme systems were stained. The results showed that: (1) Traffic pollution can dramatically change genotypic frequencies at some loci of P. annua populations. Significant deviations from HardyWeinberg equilibrium were observed on loci Fe - 1 and Me due to the excess of heterozygotes in some populations.(2) The effective number of alleles per locus and the observed and expected heterozygosity were higher in the pollution series than in the clear control site(Botanic Park population), but the increase was not related with the pollution extent. (3) Most genetic variation was found within populations, and only 6.21% was among populations of the polluted series. Slightly higher differentiation( FST = 7.98%) was observed when the control population was included. (4) The calculated gene flow(Nm) is 2.8841 per generation. The mean of genetic identity is 0.9864 and the genetic distance average to 0.0138.