典型气候环境中改性环氧树脂有机玻璃胶接性能变化规律研究

目的研究典型气候环境对两类有机玻璃胶接接头老化性能的影响。方法在重庆、青岛和拉萨三地开展两类有机玻璃胶接接头的户外自然暴露试验,研究其拉剪强度和剥离强度随老化时间的变化规律,分析气候环境因素对胶粘剂老化的作用机理,及胶接结构的老化失效模式。结果高温、高湿及紫外光辐射等气候环境因素是影响胶粘剂粘接性能的主要外在因素,其中高温高湿环境因子对其性能影响较大,而紫外光辐射引起的光降解速度并不像理论预测那样快,胶粘工艺是影响胶接接头性能的主要内在因素。结论优选出了耐候性较好,且适合航空有机玻璃和涤纶带粘接的胶粘剂,可为该胶接接头的防老化设计提供参考。     

太阳电池阵基板原子氧防护膜试验评价研究

对太阳电池阵基板用涂有有机硅／SiO2杂化涂层的Kapton膜进行的工程化应用试验评价研究进行了介绍。通过真空下材料的出气试验,对材料的总质量损失（TML）和可凝挥发物（CVCM）进行了测试。进行了温度冲击试验、粒子辐照试验,对涂层的环境耐受性进行了研究。通过原子氧试验,对带涂层薄膜的原子氧剥蚀率进行了研究。此外还对涂层薄膜进行了力学性能试验和粘接性能试验,对带涂层薄膜的拉伸强度、胶接剪切性能及与基板胶接后的剥离性能进行了测试。试验结果表明防护涂层满足工程应用的技术要求。     

某型胶粘剂加速贮存试验及寿命评估

目的评估某型胶粘剂的寿命。方法通过恒定应力试验方法对某胶粘剂进行三个不同应力量级的高温加速贮存试验。结果胶粘剂在100,80,60℃三种高温老化温度下的老化90 d后的剪切强度均明显大于初始剪切强度12.225 MPa。结论高温老化过程中,胶粘剂发生了明显的退化现象。温度越高,性能退化越快。由性能退化曲线拟合得到了胶粘剂高温老化的加速因子,评估了胶粘剂的常温贮存寿命至少为17.1年。     

高温下复合材料螺栓接头强度的试验研究

目的研究高温环境对树脂基复合材料螺栓连接接头的强度和破坏模式的影响规律。方法以T300/BMP316复合材料为研究对象,在室温~310℃范围内对不同宽孔比的螺栓连接接头开展拉伸试验研究。结果获得了不同宽孔比、不同温度环境下树脂基复合材料螺栓连接接头强度和破坏模式的变化规律。结论不同宽孔比螺栓接头试件的载荷-位移曲线既具有共性特征,又具有明显的差异。宽孔比对复合材料螺栓接头的拉伸强度和破坏模式均具有明显的影响,在相同温度下,接头的拉伸强度随着宽孔比的增大而下降,其破坏模式将由拉伸-挤压破坏逐步向剪切-挤压破坏转变,宽孔比越大,拉伸破坏模式占的比重越小,而剪切破坏占的比重越大。试验温度虽然没有改变同一宽孔比复合材料螺栓接头的破坏模式,但对其拉伸强度影响明显,相同宽孔比下复合材料螺栓接头静载强度随着温度的升高而降低,这是由于随着温度的升高,树脂基体的性能下降明显,使得接头中更易出现拉伸破坏和挤压破坏等,进而大大降低了复合材料螺栓接头的强度。     

酸性介质对橡胶材料在盐雾环境下老化行为的影响研究

目的研究SO_2、稀硫酸两种酸性介质对橡胶材料在盐雾环境下老化行为的影响。方法以乙丙橡胶、丁腈橡胶为试验对象,分别以SO_2、稀硫酸为酸性介质,开展"SO2-盐雾"、"稀硫酸-盐雾"试验,利用宏观形貌观察、拉伸性能测试方法,结合扫描电子显微镜和傅里叶红外光谱技术,分析两种酸性介质对橡胶材料老化过程的影响。结果乙丙橡胶在"SO2-盐雾"复合环境中暴露48 h后,表面由紫色变为淡蓝色;暴露12d后,表面出现密集的脱落坑和长条状的粉化带,亚甲基含量略微降低,第三单体中,残余双键特征吸收峰消失。丁腈橡胶在"SO2-盐雾"环境中暴露12d后,橡胶断裂拉伸强度保留率降低至75%,聚合物中的酰胺键、亚甲基含量显著降低。结论"SO2-盐雾"复合试验对橡胶材料的侵蚀作用更加剧烈,丁腈橡胶暴露12 d后的断裂拉伸强度损失率比在"稀硫酸-盐雾"环境下高出14.39%。SO_2气体加速了橡胶中填充剂颗粒的析出、脱落过程,造成橡胶表面出现变色、脱落等缺陷,导致橡胶材料的拉伸性能降低。     

硅橡胶低温环境性能研究

目的 研究低温环境对硅橡胶性能的影响。方法 探究硅橡胶6141和6144在-55℃长期低温环境下的压缩永久变形性能变化规律,以及不同低温环境对2种硅橡胶邵氏硬度和拉伸性能的影响,并通过DSC和TMA对材料热效应和弹性恢复行为进行分析。结果 在-55℃的低温环境下,随着时间的延长,硅橡胶的低温压缩永久变形会发生突变。当低温持续时间达到27 d后,硅橡胶6141和6144的低温压缩永久变形分别达到81%和92%,出现失效。对比-25℃和-55℃低温环境下的硬度和拉伸性能发现,随着温度的降低,材料拉断伸长率先增加、后降低,拉伸强度和硬度逐渐增大。当温度降低到-55℃时,由于材料产生结晶,硅橡胶6141和6144的拉伸强度分别增大58%和72%,稳定后的硬度值分别增加25和36。通过DSC和TMA研究发现,硅橡胶会在低温下产生结晶,回弹性降低。在-55℃低温环境下,通过TMA测试得到的6141和6144压缩永久变形分别为60%和62%。结论 在长时间的极端低温环境下,硅橡胶会缓慢发生结晶,使硅橡胶材料在高于其玻璃化转变温度和结晶温度范围内出现性能突变,发生失效。     

厌氧胶粘剂的贮存寿命试验研究

采用热空气老化加速试验,对厌氧胶粘剂的贮存寿命进行了试验研究.讨论了试验温度、试验时间对接头粘结强度的影响,分析了粘接试样的破坏类型,并分别以拉伸剪切强度下降20%、30%和50%为失效指标,评价了厌氧胶粘剂的粘接贮存寿命.     

环氧胶在亚热带湿润性气候中的老化行为研究

通过环氧树脂胶粘剂及粘接件在武汉地区的一年大气曝晒试验和力学测试、表面分析等方法,研究了环氧树脂胶粘剂在该气候环境中的老化失效行为规律.结果表明,环氧树脂胶在光照充足、高温高湿季节力学强度和表面光泽度下降较快;水、光照和温度是导致环氧树脂胶粘接失效的重要因素.     

2种终轧/开冷温度DSS 2304复合板复层组织与耐腐蚀性能对比研究

目的 对比研究2种不同终轧/开冷温度的2304/Q345C热轧双相不锈钢复合板复层组织和耐腐蚀性能。方法 分别采用金相显微镜和透射电镜观察复层组织形貌,采用铁素体测量仪分析计算复层远界面铁素体组织。分别采用化学浸泡法及电化学法测试复层抗点蚀和晶间腐蚀性能,并对其组织进行金相观察和透射分析。采用万能试验机对界面进行剪切强度测试,对界面附近进行线扫描测试分析,进一步分析剪切性能测试结果。结果 在其他热轧参数一定的情况下,终轧/开冷温度为1050/1020℃的复合板复层组织中的铁素体含量较高,奥氏体/铁素体相界更为规整,位错密度较低,晶界未发现析出相,界面剪切强度较高,复层的耐点腐蚀、晶间腐蚀及腐蚀电化学性能均较优。结论 终轧/开冷温度为1050/1020℃的热轧双相不锈钢复合板复层具有更优的耐腐蚀性能。     

燃气轮机用YS10-021聚酰亚胺三防试验验证分析

目的 研究湿热、盐雾、霉菌环境对YS10-021聚酰亚胺材料性能的影响,为燃气轮机选材设计和定寿、延寿提供数据支撑。方法 设计开展YS10-021聚酰亚胺三防试验,定期测试试样老化后的物理性能,并对试验数据进行统计分析。结果 经3552h湿热试验后,高温拉伸强度和高温弯曲强度下降24%,仍然符合出厂指标要求;常温弯曲强度下降34%,简支梁冲击强度下降62%,超出指标要求;其他各项性能未见明显老化。经3 552 h盐雾试验后,弯曲强度下降30%,其余性能均在出厂指标要求范围以内。经84 d霉菌试验后,YS10-021聚酰亚胺各项性能均有轻微下降趋势,但老化不明显。结论 YS10-021聚酰亚胺在湿热、盐雾、霉菌环境中的耐受性良好。总体来看,湿热和盐雾环境对YS10-021聚酰亚胺力学性能的影响更大。     

Effects of two sludge application on fractionation and phytotoxicity of zinc and copper in the soil

The potential harm of heavy metals is a primary concern in application of sludge to the agricultural land. A pot experiment was conducted to evaluate the effect of two sludges on fractionation of Zn and Cu in soil and their phytotoxicity to pakchoi. The loamy soil was mixed with 0%, 20%, 40%, 60% and 80% (by weight) of digested sewage sludge (SS) and composted sludge (SC). The additions of both sludges caused a significant raise in all fractions, resulting in that exchangeable (EXCH) and organic bound (OM) became predominance of Zn and organic bound Cu occupied the largest portion. There was more available amount of Zn and Cu in SS treatments than SC treatments. During the pot experiment, the concentration of Zn in EXCH, carbonate (CAR) and OM and Cu in EXCH and OM fractions decreased in all treatments, so their bioavailability reduced. Germination rate and plant biomass decreased when the addition rate was high and the best yield appeared in 20% mixtures at the harvest of pakchoi. The two sludges increased tissue contents of Zn and Cu especially in the SS treatments. Zn in pakchoi was not only in relationship to ΔEXCH and ΔCAR forms but also in ΔOM forms in the sludge-soil mixtures. Tissue content of Cu in pakchoi grown on SC-soils could not be predicted by ΔEXCH. These correlation rates between Zn and Cu accumulation in pakchoi and variation of different fractions increased with time, which might indicate that sludges represented stronger impacts on the plant in long-term land application.     

Intraspecific differences in effects of co-contamination of cadmium and

A hydroponic experiment was carried out to study intraspecific differences in the effects of different concentrations of cadmium (Cd)(0-10 mg/L) and arsenate (As(V)) (0-8 mg/L) on the growth parameters and accumulation of Cd and As in six wheat varieties Jing-9428, Duokang-1, Jingdong-11, Jing-411, Jingdong-8 and Zhongmai-8. The endpoints of wheat seedlings, including seed germination,biomass, root length and shoot height, decreased with increasing the Cd and As concentrations. Significant differences in seed germination, biomass, root length, shoot height and the accumulation of Cd and As were observed between the treatments and among the varieties (p ＜ 0.05). The lethal dosage 50% were about 20, 80, 60, 60, 80 and 20 mg As/L for Jing-9428, Duokang-1, Jingdong-11,Jing-411, Jingdong-8 and Zhongmai-8, respectively, and the corresponding values for Cd were about 30, 80, 20, 40, 60 and 10 mg Cd/L, respectively. Among the six varieties, Duokang-1 was found to be the most resistant to Cd and As toxicity, and Zhongmai-8 was the most sensitive to Cd and As co-contamination. The resistance of the six varieties was found dependant on the seedling uptake of Cd and As. Duokang-1 was the most suitable for cultivation in Cd and As co-contaminated soils.     

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.     

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.     

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.     

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.     

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.