5083铝合金在淡海水交替自然环境中的腐蚀行为研究

目的研究5083铝合金在淡海水交替自然环境下的耐蚀性能。方法参照GB/T 5776,分别在淡海水交替、海水及淡水自然环境中开展5083铝合金2年的耐浸泡试验。采集每周期试验样品的腐蚀数据,并进行5083铝在三种自然水环境下的耐蚀性能比对。采用腐蚀电位、交流阻抗等电化学方法,对其耐蚀性能进行评价。结果 5083铝在淡海水交替自然环境下腐蚀严重,腐蚀速率是海水环境下的5.3倍,是淡水环境下的15.8倍。点蚀密度最大,平均点蚀深度是海水环境下的2.6倍,是淡水环境下的1.7倍。结论 5083铝在淡海水交替自然环境下的耐蚀性差,并从电化学试验结果上得到很好的验证。     

纳米涂层/铝合金在不同pH值的海水溶液中的腐蚀行为研究

目的评价纳米涂层/铝合金在不同pH值海水溶液中的腐蚀行为。方法通过测试纳米涂层/铝合金试样在不同pH值海水溶液中的EIS值,分析试样阻抗谱图及Bode谱图的演化规律,建立不同EIS图谱的不同电极阻抗模型,并采用ZView软件解析涂层体系不同时期的电化学阻抗谱,获得涂层电阻的变化趋势,及不同pH值海水浸泡的纳米涂层体系腐蚀失效速度。结果随着浸泡时间的增加及pH值的降低,纳米涂层/铝合金体系腐蚀损伤失效速率在浸泡前期整体趋势增大,但中后期由于腐蚀产物逐渐堵塞了涂层的微孔,腐蚀介质向铝合金表面渗透的速率逐渐减小。结论 pH为2.0海水浸泡下的3涂层失效最快,其次是pH为4.0海水浸泡下的2涂层,最后为p H为6.0海水浸泡下的1涂层,该涂层体系应采用等效电路模型C进行拟合。     

钼酸钠对靶用 5083 铝合金耐蚀性能影响的研究

目的提高靶用5083铝合金材料的耐蚀性。方法分别运用阳极极化、交流阻抗及EDS等试验技术研究钼酸钠对5083铝合金在3%氯化钠溶液中的耐蚀性能影响。结果钼酸钠加入3%氯化钠溶液以后,该铝合金的腐蚀电位下降,点蚀电位与腐蚀电位分离,维钝电流减小,阻抗值增大,抗点蚀能力提高。结论钼酸钠对5083铝合金产生缓蚀作用。     

5083铝合金在3%NaCl溶液中的微区电化学特性

目的对5083铝合金在海水环境下的腐蚀行为进行深入的探索。方法在3%Na Cl溶液条件下,通过扫描振动电极技术(SVET)对5083铝合金的微小区域进行了原位测量,得到表面区域电位梯度的变化情况,结合交流阻抗测试,以及扫描电镜和能谱分析等方法,研究5083铝合金腐蚀的发生、发展机理。结果由于Zn和S等元素的偏析,腐蚀过程中,夹杂物等第二相周围优先溶解,致使铝合金基体裸露在溶液中。随着反应的持续形成点蚀,腐蚀电流使腐蚀区域的电位高于基体电位。浸泡3 h,最大电位差为15.72 m V,浸泡5 h,最大电位差达到20.06 m V。结论 5083铝合金在海水环境下夹杂物的周围优先溶解,然后是电位高于基体电位的第二相发生溶解,同时钝化膜破裂处也发生腐蚀,最终这些区域形成点蚀。     

铝及铝合金在自然水环境中的腐蚀行为对比研究

目的 分析研究铝及铝合金在自然水环境中的腐蚀行为。方法 通过开展LM3纯铝、5083铝、LF6M去包铝及带包铝在淡海水交替、海水及淡水自然环境下2 a的暴露试验,将3种环境下材料的腐蚀形貌、腐蚀速率进行对比。总结4种铝及铝合金材料在不同水环境下的腐蚀规律,对其腐蚀机理进行简要的探讨,并对其长周期的腐蚀行为进行预测。结果 通过对4种材料局部腐蚀协同影响因子(b)的对比可以发现,淡水环境对LM3纯铝局部腐蚀的影响最大,淡海水环境对5083铝合金局部腐蚀影响最大,淡水及淡海水环境对2种LF6M铝合金材料局部腐蚀的影响都很大。结论 5083、LF6M带包铝及去包铝,在淡海水交替自然环境下的耐蚀性能最差,LM3纯铝在淡水环境下耐蚀性能最差。     

温度与循环热冲击对聚酰亚胺涂层耐蚀性影响

目的研究聚酰亚胺涂层对N80钢的防腐性能和耐热冲击性能。方法采用静电粉末喷涂在N80钢表面获得一种聚酰亚胺防腐涂层,通过高温浸泡实验评价涂层在不同温度下、不同腐蚀介质中的耐蚀性能,通过循环热冲击实验评价涂层的耐热冲击性能,通过扫描电子显微镜(SEM)观察实验前后涂层的表面微观形貌。结果热重分析(TGA)表明,聚酰亚胺涂层的热分解温度(t_(d5))为518℃。电化学交流阻抗测试结果和SEM形貌观测表明,腐蚀介质温度越高,耐蚀性能下降越快,涂层在3.5%Na Cl溶液的耐蚀性能比在25%HCl溶液中更好。涂层在经过不同温度的循环热冲击之后,表面无破损。结论聚酰亚胺涂层具有优异的耐热冲击性能,温度和腐蚀介质对涂层的耐蚀性能有重要影响。     

温度和溶解氧对5083铝合金海水腐蚀性的影响

采用动电位极化和电化学阻抗试验方法,研究了温度和溶解氧对5083铝合金在海水中腐蚀电化学性能的影响。结果表明,随着溶解氧浓度的降低,铝合金自腐蚀电位负移;随着温度的增加,铝合金点蚀电位负移,阴极过程受扩散控制。腐蚀微观形貌分析表明铝合金在高温高氧状态下主要以均匀腐蚀为主,而在低温低氧状态下发生了明显点蚀。     

军绿有机涂层破损腐蚀行为研究

目的研究不同破损程度下军绿有机涂层的腐蚀行为,确定破损率对其防护性能变化的影响。方法通过人工制作不同的破损率,并利用电化学阻抗谱技术,研究不同破损程度下军绿有机涂层的电化学特征。结果根据不同破损程度下的军绿有机涂层的电化学特征,确定了涂层从完好到失效的四个阶段,初始完好阶段(破损率K≤0.0004%)、破损增大阶段(0.0016%K≤0.04%)、破损过大阶段(0.16%K≤1%)和失效阶段(4%K≤16%)。结论破损率K为0.04%的点是该涂层防护性能急转直下的转折点,因此破损率K大于0.04%时,应及时对车辆表面涂层进行修补和防护。     

2024-T62铝合金涂层外场腐蚀环境下电化学性能研究

目的评估自然暴露条件下涂层的耐蚀性能。方法选取西沙热带海洋环境作为自然暴晒场,开展2024-T62铝合金涂层(N1和N2)在湿热暴露、紫外照射、盐雾等综合腐蚀环境下的外场暴晒试验,利用电化学测试方法对暴晒后涂层在3.5%Na Cl溶液中浸泡不同时间的耐蚀性能进行研究。结果铝合金涂层外场暴晒试验后,电化学阻抗值下降,综合腐蚀环境具有显明的加速作用。随着在3.5%Na Cl溶液的浸泡时间增加,C_(coat)-T值不断增大,Rcoat值不断减小。结论 N1铝合金涂层暴晒件电化学阻抗值较高,具有较强的耐蚀性能。     

流动海水环境中人工破损有机涂层的劣化过程研究

目的研究流动海水环境中人工破损有机涂层的劣化过程。方法使用电化学阻抗谱(EIS)技术对比研究流动海水与静止海水环境中破损涂层的劣化行为,跟踪观察涂层宏观形貌演变。结果根据EIS响应特征,发现流动海水中的人工破损有机涂层劣化更快,且在浸泡后期流动海水中破损涂层没有形成扩散阻抗。根据涂层宏观形貌发展,发现静止海水中涂层仅围绕破损处出现了面积较小的锈点和鼓泡,而流动海水中涂层因劣化而产生的锈点和鼓泡面积更大且大量分布在整个涂层表面。结论当人工破损有机涂层在流动海水和静止海水环境的浸泡过程中,涂层劣化首先从人工破损处开始。破损处成为局部腐蚀反应主要的阳极区,破损处周围的区域和涂层内在缺陷处成为扩展腐蚀反应的阴极区。流动海水中涂层的腐蚀产物累积与脱落更加频繁,导致涂层劣化速度加快和基体金属腐蚀加剧。     

Evaluation of phytoextracting cadmium and lead by sunflower, ricinus, alfalfa and mustard in hydroponic culture

Soil contaminated with heavy metals cadmium(Cd)and lead(Pb)is hard to be remediated.Phytoremediation may be a feasible method to remove toxic metals from soil,but there are few suitable plants which can hyperaccumulate metals.In this study,Cd and Pb accumulation by four plants including sunflower(Helianthus annuus L.),mustard(Brassica juncea L.),alfalfa(Medicago sativa L.), ricinus(Ricinus communis L.)in hydroponic cultures was compared.Results showed that these plants could phytocxtract heavy metals, the ability of accumulation differed with species,concentrations and categories of heavy metals.Values of BCF(bioconcentration factor)and TF(translocation factor)indicated that four species had dissimilar abilities of phytoextraction and transportation of heavy metals.Changes on the biomass of plants,pH and Eh at different treatments revealed that these four plants had distinct responses to Cd and Pb in cultures.Measurements should be taken to improve the phytoremediation of sites contaminated with heavy metals,such as pH and Eh regulations,and so forth.     

Oxidation of As(Ⅲ) by potassium permanganate

The oxidation of As(Ⅲ) with potassium permanganate was studied under conditions including pH, initial As(Ⅲ) concentration and dosage of Mn(Ⅶ). The results have shown that potassium permanganate was an effective agent for oxidizing of As(Ⅲ) in a wide pH range. The pH value of tested water was not a significant factor affecting the oxidation of As(Ⅲ) by Mn(Ⅶ). Although theoretical redox analyses suggest that Mn(Ⅶ) should have better performance in oxidization of As(Ⅲ) within lower pH ranges, the experimental results show that the oxidation efficiencies of As(Ⅲ) under basic and acidic conditions were similar, which may be due to the adsorption of As(Ⅲ) on the Mn(OH)2 and MnO2 resulting from the oxidation of As(Ⅲ).     

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.     

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.     

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.     

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.     

Chlorobenzenes in waterweeds from the Xijiang River （Guangdong section） of the Pearl River

The Xijiang River is the major source of water for about 4.5 millions of urban population and 28.7 millions of rural population. The water quality is very important for the health of the rural population. The concentration and distribution of chlorobenzenes (CBs) in both water and waterweeds collected from 4 stations in the Xijiang River (Gangdong section) of the Pearl River in April and November were determined. The result showed that nearly every congener of CBs was detected. The total contents of CBs (∑CBs) in the river water ranged from 111.1 to 360.0 ng/L in April and from 151.9 to 481.7 ng/L in November, respectively. The pollution level of CBs in the water in April was higher than that in November. The contents of ∑ CBs in waterweeds ranged from 13.53×102 μg/g to 38.27×102μg/g dry weight (dw). There was no significant difference between April and November in waterweeds. The distribution of CBs in roots, caulis, and leaves of Vallisneria spiralis L. showed different patterns. The leaves mainly contained low-molecular-weight CBs(DCBs), whereas the roots accumulated more PCBs and HCBs. The average lgBCFlip (bioconcentration factor) of CBs ranged from 0.64 to 3.57 in the waterweeds. The spatial distribution character of CBs in the Xijiang River was: Fengkai County ＜ Yunan County ＜Yun'an County ＜ Gaoyao County according to the ∑CBs, and the pollution deteriorated from the upstream to the downstream of the Xijiang River. Further analysis demonstrated that the discharge of waste containing CBs may be the main source of CBs pollution in the Xijiang River.     

Degradation of 2,4-dichlorophenol with a novel TiO2/Ti-Fe-graphite felt photoelectrocatalytic oxidation process

Degradation of 2,4-dichlorophenol(2,4-DCP)was studied in a novel three-electrode photoelectrocatalytic(PEC)integrative oxidation process,and the factors influencing the degradation rate,such as applied current,flow speed of O_2,pH,adscititious voltage and initial 2,4-DCP concentration were investigated and optimized.H_2O_2 was produced nearby cathode and Fe~(2 )continuously generated from Fe anode in solution when current and O_2 were applied,so,main reactions,H_2O_2-assisted TiO_2 PEC oxidation and E-Fenton reaction,occurred during degradation of 2,4-DCP in this integrative system.The degradation ratio of 2,4-DCP was 93% in this integrative oxidation process,while it was only 31% in E-Fenton process and 46% in H_2O_2-assisted TiO_2 PEC process.So,it revealed that the degradation of 2,4-DCP was improved greatly by photoelectrical cooperation effect.By the investigation of pH,it showed that this integrative process could work well in a wide pH range from pH 3 to pH 9.     

Effect of copper on the degradation of pesticides cypermethrin and cyhalothrin

The influence of coexisting copper (Cu) ion on the degradation of pesticides pyrethroid cypermethrin and cyhalothrin in soil and photodegradation in water system were studied.Serial concentrations of the pesticides with the addition of copper ion were spiked in the soil and incubated for a regular period of time,the analysis of the extracts from the soil was carried out using gas chromatography (GC).The photodegradation of pyrethroids in water system was conducted under UV irradiation.The effect of Cu~(2 ) on the pesticides degradation was measured with half life (t_(0.5)) of degradation.It was found that a negative correlation between the degradation of the pyrethroid pesticides in soil and Cu addition was observed.But Cu~(2 ) could accelerate photodegradation of the pyrethroids in water.The t_(0.5) for cyhalothrin extended from 6.7 to 6.8 d while for cypermethrin extended from 8.1 to 10.9 d with the presence of copper ion in soil.As for photodegradation,t_(0.5) for cyhalothrin reduced from 173.3 to 115.5 rain and for cypermethrin from 115.5 to 99.0 min.The results suggested that copper influenced the degradation of the pesticides in soil by affecting the activity of microorganisms.However, it had catalyst tendency for photodegradation in water system.The difference for the degradation efficiency of pyrethroid isomers in soil was also observed.Copper could obviously accelerate the degradation of some special isomers.     

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.