在污染大气环境中NaCl对镁合金的协同作用

研究了沉积NaC l的AZ91D镁合金在含有SO2和CO2的模拟污染大气环境中初期腐蚀行为。研究了在SO2和CO2协同作用下,表面沉积NaC l的AZ91D镁合金大气初期腐蚀规律。采用扫描电子显微镜(SEM)观察表面腐蚀形貌,XRD进行腐蚀产物分析。结果表明,由于NaC l的沉积加速了AZ91D镁合金的初期大气腐蚀,SO2、CO2和NaC l多种因素协同作用对AZ91D镁合金的初期大气腐蚀的影响远大于单一SO2、CO2和NaC l因素。     

四硼酸钠对AZ91D镁合金的缓蚀效果研究

选用无机环保型缓蚀剂四硼酸钠,研究了质量浓度不同的四硼酸钠对AZ91D镁合金的缓蚀效果,并采用电子显微镜对空白样品及添加缓蚀剂浸泡样品的腐蚀形貌进行了分析。结果表明,在室温下,四硼酸钠对AZ91D镁合金具有缓蚀效果,四硼酸钠溶液质量浓度为2. 4 g/L时的缓蚀效率可达到66. 46%;浸泡腐蚀与电化学腐蚀结果一致。     

环境作用动力学在应力腐蚀断裂中的应用

目的研究材料的应力腐蚀断裂时间。方法应用环境作用动力学理论,求解材料的应力腐蚀断裂时间函数。结果从环境作用动力学理论得到了材料的应力腐蚀断裂时间函数,并对AZ61和AZ80镁合金进行了试验验证。结论环境作用动力学理论可以描述镁合金材料应力腐蚀断裂时间;AZ61镁合金抗应力腐蚀性能优于AZ80镁合金。     

AZ31B镁合金挤压工艺研究

在油炉中熔炼AZ31B镁合金 ,用熔剂保护 ,石墨模铸造圆锭。铸锭经 40 0℃× 1 2h的均匀化处理后 ,进行热挤压 ,其挤压温度为 40 0℃ ,挤压速度为 1～ 2 .5m/min ,挤压比为 1 0～ 45。共挤出了 1 1种规格的棒材、管材、型材 (工字型、槽型、角形、方形、T形等 ) ,挤压过程中均发生了动态再结晶 ,其抗拉强度σb 在 2 75～ 2 85MPa之间 ,屈服强度σ0 .2　在 2 2 0～ 2 2 5MPa之间 ,延伸率δ在 1 5 %～ 1 7%之间。所制订的工艺合理 ,挤压出的棒材、管材、型材有较好的力学性能     

镁合金在模拟污染气体环境中的初期腐蚀规律

研究了在含有SO2和CO2的模拟污染大气环境中AZ91D镁合金大气腐蚀初期行为,讨论了在SO2和CO2协同作用下AZ91D镁合金大气初期腐蚀规律。采用扫描电子显微镜（SEM）观察表面腐蚀形貌,XRD进行腐蚀产物分析。结果表明由于SO2和CO2的溶解导致电解液膜酸性增加,进一步加大了表面的反应活性．加速了大气初期腐蚀。     

乙酰螺旋霉素废水生物处理的试验研究

采用相同体积 (6 2L)的升流厌氧污泥床和厌氧复合床处理乙酰螺旋霉素废水 ,当容积负荷为 6 0kg(COD) (m3 ·d)时 ,升流厌氧污泥床和厌氧复合床反应器对SS、COD、BOD5的去除率分别为 6 7 4 %、85 1%、91 2 %和 75 6 %、91 7%、96 1%,结果表明厌氧复合床是高效实用的厌氧生物反应器 ;厌氧出水采用相同体积 (6 4L)的生物接触氧化工艺和周期循环活性污泥系统进行处理 ,当容积负荷为 1 6kg(COD) (m3 ·d)时 ,生物接触氧化反应器和周期循环活性污泥系统对SS、COD、BOD5的去除率分别为 87 9%、85 1%、92 8%和 91 6 %、88 7%、95 4 %,结果表明周期循环活性污泥系统是高效实用的好氧生物反应器 .     

食用菌菌丝对校园生活污水净化效果研究

采用平菇菌丝体对校园生活污水进行净化处理,通过测定净化过程中生活污水p H、COD、BOD5、总磷、总氮的变化,探索食用菌菌丝对校园生活污水的净化作用。结果表明:食用菌菌丝体对校园生活污水净化有一定的效果,生活污水中的COD和BOD5去除率分别达到79. 91%、91. 55%,但对校园生活污水中总氮和总磷的去除效果不理想;平菇菌丝体的接种量对校园生活污水的净化效果有一定的影响,本实验选择菌丝体3个接种量:3%、5%、10%对生活污水的净化效果表现为3% 5% 10%。     

环氧富锌涂层对AZ91D镁合金的腐蚀防护能力研究

目的研究环氧富锌涂层对AZ91D镁合金的腐蚀防护能力。方法采用机械喷涂法在AZ91D镁合金表面制备一种保护性的环氧富锌涂层。采用电化学阻抗谱(EIS)研究环氧富锌涂层在0.5 mol/L的Na2SO4腐蚀溶液中的电化学腐蚀行为及其对镁合金的腐蚀防护能力。结果浸泡初期,环氧富锌涂层的阻抗谱中只出现一个时间常数,暗示着环氧富锌涂层优异的阻挡层作用;浸泡48 h后,环氧富锌涂层阻抗谱中出现两个时间常数,高频和低频时间常数分别对应环氧富锌涂层中高聚合的介电性质和锌粉的活性溶解;浸泡336 h后,环氧富锌涂层仍具有很高的阻抗模值,表明此时环氧富锌涂层对镁合金仍能提供良好的腐蚀防护。结论环氧富锌涂层在0.5 mol/L Na2SO4腐蚀溶液中能对AZ91D镁合金提供很好的腐蚀防护。     

飞机起落架支柱固定螺栓环境氢脆断裂研究

某飞机起落架缓冲支柱固定螺栓长期使用后断裂.为了确定该螺栓断裂的原因,对断裂螺栓进行了外观检查,断口宏观、微观分析,能谱仪成分分析,金相组织检查、硬度检测以及氢含量测定,结果表明:断裂螺栓的断口具有氢脆断裂特征,其断裂失效性质为环境氢脆断裂;飞机服役期间,螺栓保护不良,致使环境对螺栓造成了腐蚀,腐蚀产生的氢进入螺栓是导致螺栓产生环境氢脆裂纹的根本原因.对螺栓进行保护可有效地避免该类故障的重复发生.     

某型装甲车底盘系统平衡肘断裂分析

目的 探讨平衡肘断裂原因,消除故障隐患和防止类似问题发生。方法 采用单反相机、扫描电镜、金相显微镜、硬度计、电感耦合等离子体原子发射光谱仪等对平衡肘故障件的宏观形貌、微观形貌、显微组织、硬度、化学成分等开展表征分析。利用ANSYS有限元软件对内花键进行应力分析,并对2次淬火的试样尺寸进行测量。结果 右4平衡肘裂纹源断口为撕裂和沿晶的混合断裂,断口芯部为解理断裂;右2平衡肘断口内表层淬火层为沿晶和韧窝的混合断裂,芯部为韧性断裂。故障件显微组织和化学成分均无明显变化,仅表面硬度值较实验前降低了7%~9%。断裂失效原因是由于内花键二次高频淬火后收缩变形,齿根圆弧部位在腐蚀介质和交变载荷的共同作用下因应力集中而形成裂纹,在后期循环应力作用下,裂纹继续扩展导致疲劳断裂。结论 从加强腐蚀控制和热处理的角度出发,通过选用抗腐蚀性能好的材料、进行表面防护处理、控制车体环境的湿度和温度等加强腐蚀控制,并增加采用电脉冲等方式对变形花键齿进行修形工序严格控制尺寸范围,避免产生过大拉应力,确保装备质量。     

EDTA-enhanced phytoremediation of lead contaminated soil by Bidens maximowicziana

Phytoremediation is a potential cleanup technology for the removal of heavy metals from contaminated soils.Bidens maximowicziana is a new Pb hyperaccumulator,which not only has remarkable tolerance to Pb but also extraordinary accumulation capacity for Pb.The maximum Pb concentration was 1509.3 mg/kg in roots and 2164.7 mg/kg in overground tissues.The Pb distribution order in the B. maximowicziana was:leaf>stem>root.The effect of amendments on phytoremediation was also studied.The mobility of soil Pb and the Pb concentrations in plants were both increased by EDTA application.Compared with CK(control check),EDTA application promoted translocation of Pb to overground parts of the plant.The Pb concentrations in overground parts of plants was increased from 24.23-680.56 mg/kg to 29.07-1905.57 mg/kg.This research demonstrated that B.maximowicziana appeared to be suitable for phytoremediation of Pb contaminated soil,especially,combination with EDTA.     

Distribution and ecological effect of mercury in Laogang landfill, Shanghai, China

Laogang landfill near Shanghai is the largest landfill in China, and receives about 10000 t of daily garbage per day, Samples of topsoil and plants were analyzed to evaluate mercury pollution from the landfill. For topsoil samples, there were significant correlations among total mercury （HgT）, combinative mercury （Hgc） and gaseous mercury （HgG）, and content of total organic carbon （TOC）, but, no significantly relationship was found between Hg content and filling time. Hg content changes in vertical profiles with time showed that the average Hgv of profiles 1992, 1996, and 2000 was similar, but their average HgG was quite different. HgT was significantly correlated with Hgc in profile 1992 and 2000, and Hgv was significantly correlated with Hg6 in profile 1996. HgG/Hgv ratio in profile samples decreased in the order of （HgG,/HgT）1992〉（HgG/HgT）1996〉〉（HgG/HgT）2000. A simple outline of Hg release in landfill could be drawn： with increasing of filling time, degradation undergoes different biodegradation, accordingly, gaseous mercury goes through small, more, and small proportion to total mercury. Distribution of Hg in plants was inhomogeneous, following the order of leaf〉root〉stem. The highest value of leaf may be associated with higher atmospheric Hg from landfill. Ligneous plants （e.g. Phyllostachys glanca, Prunus salicina and Ligustrum lucidum） are capable of enriching more Hg than herbaceous plants.     

Toxic effects of acetochlor, methamidophos and their combination on nifH gene in soil

Toxic effects of two agrochemicals on nifH gene in agricultural black soil were investigated using denaturing gradient gel electrophoresis （DGGE） and sequencing approaches in a microcosm experiment. Changes of soil nifH gene diversity and composition were examined following the application of acetochlor, methamidophos and their combination. Acetochlor reduced the nifH gene diversity （both in gene richness and diversity index values） and caused changes in the nifH gene composition. The effects of acetochlor on nifH gene were strengthened as the concentration of acetochlor increased. Cluster analysis of DGGE banding patterns showed that nifH gene composition which had been affected by low concentration of acetochlor （50 mg/kg） recovered firstly. Methamidophos reduced nifH gene richness that except at 4 weeks. The medium concentration of methamidophos （150 mg/kg） caused the most apparent changes in nifH gene diversity at the first week while the high concentration of methamidophos （250 mg/kg） produced prominent effects on nifH gene diversity in the following weeks. Cluster analysis showed that minimal changes of nifH gene composition were found at 1 week and maximal changes at 4 weeks. Toxic effects of acetochlor and methamidophos combination on nifH gene were also apparent. Different nifH genes （bands） responded differently to the impact of agrochemicals： four individual bands were eliminated by the application of the agrochemicals, five bands became predominant by the stimulation of the agrochemicals, and four bands showed strong resistance to the influence of the agrochemicals. Fifteen prominent bands were partially sequenced, yielding 15 different nifH sequences, which were used for phylogenetic reconstructions. All sequences were affiliated with the alpha- and beta-proteobacteria, showing higher similarity to eight different diazotrophic genera.     

Enzymatic oxidation of aqueous pentachlorophenol

The influence of the nonionic surfactant Tween 80 on pentachlorophenol （PCP） oxidation catalyzed by horseradish peroxidase was studied. The surfactant was tested at concentrations below and above its critical micelle concentration （CMC）. Enhancement of PCP removal was observed at sub-CMCs. The presence of Tween 80 in the reaction mixture reduced enzyme inactivation which occurred through a combination of free radical attack and sorption by precipitated products. A simple first-order model was able to simulate time profiles for enzyme inactivation in the presence or absence of Tween 80. At supra-CMCs, the surfactant caused noticeable reductions in PCP removal, presumably through micelle partitioning of PCP which precluded the hydrophobic PCP molecule from interacting with the enzyme.     

Decomposition of alachlor by ozonation and its mechanism

Decomposition and corresponding mechanism of alachlor, an endocrine disruptor in water by ozonation were investigated. Results showed that alachlor could not be completely mineralized by ozone alone. Many intermediates and final products were formed during the process, including aromatic compounds, aliphatic carboxylic acids, and inorganic ions. In evoluting these products, some of them with weak polarity were qualitatively identified by GC-MS. The information of inorganic ions suggested that the dechlorination was the first and the fastest step in the ozonation of alachlor.     

Arsenic uptake by arbuscular mycorrhizal maize （Zea mays L.） grown in an arsenic-contaminated soil with added phosphorus

The effects of arbuscular mycorrhizal (AM) fungus (Glomus mosseae) and phosphorus (P) addition (100 mg/kg soil) on arsenic (As) uptake by maize plants (Zea mays L.) from an As-contaminated soil were examined in a glasshouse experiment.Non-mycorrhizal and zero-P addition controls were included.Plant biomass and concentrations and uptake of As,P,and other nutrients,AM colonization,root lengths,and hyphal length densities were determined.The results indicated that addition of P significantly inhibited root colonization and development of extraradical mycelium.Root length and dry weight both increased markedly with mycorrhizal colonization under the zero-P treatments,but shoot and root biomass of AM plants was depressed by P application.AM fungal inoculation decreased shoot As concentrations when no P was added,and shoot and root As concentrations of AM plants increased 2.6 and 1.4 times with P addition,respectively.Shoot and root uptake of P,Mn,Cu,and Zn increased,but shoot Fe uptake decreased by 44.6%,with inoculation, when P was added.P addition reduced shoot P,Fe,Mn,Cu,and Zn uptake of AM plants,but increased root Fe and Mn uptake of the nonmycorrhizal ones.AM colonization therefore appeared to enhance plant tolerance to As in low P soil,and have some potential for the phytostabilization of As-contaminated soil,however,P application may introduce additional environmental risk by increasing soil As mobility.     

Degradation of metabolites accumulated of benzo[a]pyrene by coupling Penicillium Chrysogenum with KMnO4

Several main metabolites of benzo[a]pyrene （BaP） formed by Penicillium chrysogenum, Benzo[a]pyrene-1,6-quinone （BP 1,6- quinone）, trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene （BP 7,8-diol）, 3-hydroxybenzo[a]pyrene （3-OHBP）, were identified by high-performance liquid chromatography （HPLC）. The three metabolites were liable to be accumulated and were hardly further metabolized because of their toxicity to microorganisms. However, their further degradation was essential for the complete degradation of BaP. To enhance their degradation, two methods, degradation by coupling Penicillium chrysogenum with KMnO4 and degradation only by Penicillium chrysogenum, were compared; Meanwhile, the parameters of degradation in the superior method were optimized. The results showed that （1） the method of coupling Penicillium chrysogenum with KMnO4 was better and was the first method to be used in the degradation of BaP and its metabolites; （2） the metabolite, BP 1,6-quinone was the most liable to be accumulated in pure cultures; （3） the effect of degradation was the best when the concentration of KMnO4 in the cultures was 0.01% （w/v）, concentration of the three compounds was 5 mg/L and pH was 6.2. Based on the experimental results, a novel concept with regard to the bioremediation of BaP-contaminated environment was discussed, considering the influence on environmental toxicity of the accumulated metabolites.     

Impact of atrazine and nitrogen fertilizers on the sorption of chlorotoluron in soil and model sorbents

Sorption of chlorotoluron in ammonium sulfate, urea and atrazine multi-solutes system was investigated by batch experiments. The results showed application of nitrogen fertilizers to the soil could affect the behavior of chlorotoluron. At the same concentration of N, sorption of chlorotoluron decreased as the concentration of atrazine increased on the day 0 and 6 in soil, respectively. The sorption of chlorotoluron increased from 0 to 6 d when soils were preincubated with deionized water, ammonium sulfate and urea solution for 6 d. That indicated incubation time was one of the most important factors for the sorption of chlorotoluron in nitrogen fertilizers treatments. The individual sorption isotherms of chlorotoluron in rubbery polymer and silica were strictly linear in single solute system, but there were competition sorption between pesticides or between pesticides and nitrogen fertilizers. That indicated the sorption taken place by concurrent solid-phase dissolution mechanism and sorption on the interface of water-organic matter or water-mineral matter.     

基于综合水质标识指数和对应分析法的校园河道水质评价

以三峡大学的校园河道求索溪为研究对象,利用综合水质标识指数法确定求索溪水质类别,分析其水质时空变化规律,并利用对应分析法得出求索溪中不同监测点的主要污染因子.研究结果表明:求索溪整体的综合水质标识指数为7.423,整体水质为劣V类(地表水环境质量标准GB 3838-2002)且黑臭.从时间变化来看,求索溪4月份的水质最差,5月份次之,4、5月份所有监测点的水质都劣于V类且黑臭;8月份水质最好,水质为Ⅳ类;从空间分布来看,8个监测点综合水质标识指数均超过6.0,水质为劣V类,其中6号监测点的水质相对最好,监测点3号的水质相对最差;对应分析法得出求索溪的整体水体污染程度受总氮因子的影响最大,其次为总磷.该研究拟为求索溪及类似校园河道的水环境治理研究提供基础依据和参考.     

Effects of chitosan on growth of an aquatic plant (Hydrilla verticillata) in polluted waters with different chemical oxygen demands

Effects of chitosan on a submersed plant, Hydrilla verticillata, were investigated. Results indicated that H. venicillata could prevent ultrastructure phytotoxicities and oxidativereaction from polluted water with high chemical oxygen demand (COD). Superoxide dismutase (SOD) activity and malondialdehyde (MDA) contents in H. verticillata treated with 0.1% chitosan in wastewater increased with high COD (980 mg/L) and decreased with low COD (63 mg/L), respectively. Ultrastructural analysis showed that the stroma and grana of chloroplast basically remained normal. However, plant cells from the control experiment (untreated with chitosan) were vacuolated and the cell interval increased. The relict of protoplast moved to the center, with cells tending to disjoint. Our findings indicate that wastewater with high COD concentration can cause a substantial damage to submersed plant, nevertheless, chitosan probably could alleviate the membrane lipid peroxidization and ultrastructure phytotoxicities, and protect plant cells from stress of high COD concentration polluted water.