新型防腐涂层对直升机典型结构材料防护性能研究

目的研究新型防腐涂层对直升机典型结构用铝合金及复合材料在热带海洋性气候环境下的防护性能,并与原防护涂层进行对比。方法通过测试涂层腐蚀后的形貌、光泽度、色差、电化学阻抗等,对比新/原涂层对直升机典型结构用铝合金和复合材料的防护性能。结果经过2年腐蚀后,新涂层表面无明显变化,而原涂层表面有轻微腐蚀,光泽度和色差下降较大。电化学阻抗测试表明,暴露前后涂层结构无明显变化,涂层阻抗值呈现持续下降的趋势,但是原涂层阻抗下降更快。结论新涂层对直升机典型铝合金和复合材料有更好的防护性,更加适于海洋性环境的使用。     

30CrMnSiA合金钢3种涂层体系耐蚀性研究

目的研究西沙海洋环境下30CrMnSiA合金钢三种(C1,C2,C3)涂层体系的耐腐蚀性能。方法在西沙海域环境开展30CrMnSiA合金钢三种涂层的自然暴晒实验,暴晒实验时间为3年,分别通过测试光泽度、色差、电化学阻抗值等手段检测腐蚀状况来研究腐蚀特点。结果三种涂层的光泽度和色差随着时间的增长逐渐减少,暴晒后三种涂层的光泽度和色差相差不大,但三种涂层检测的电化学阻抗值相差很大,且C1涂层阻抗值明显大于C2和C3涂层。结论 C1涂层体系相较于C2和C3两种涂层体系有更高的耐腐蚀性能。     

车辆装备涂层局部微小破损对防护性能的影响研究

目的探究车辆装备有机涂层在微小破损之后性能的变化情况,并通过完好涂层防护能力的对比分析,间接预测微小破损涂层的服役寿命。方法利用某型现役装备涂层作为试验样本,进行综合环境下的循环加速腐蚀试验,最后利用EIS分析实验数据,分析两者防护性能的差别。结果完好涂层与破损涂层的防护性能均出现了大幅度的下降,两者在经过10个周期的腐蚀试验之后,都失去了防护能力,出现了大面积锈迹。完好涂层的低频阻抗模值|Z|0.1 Hz在试验初期处于1010Ω·cm2数量级,最后下降到106Ω·cm2以下;初始状态破损涂层的低频阻抗模值|Z|0.1 Hz为1.2×105Ω·cm2,9个腐蚀周期之后下降至5.7×103Ω·cm2,下降了2个数量级。结论破损涂层在腐蚀初期更多地表现出电容性质,其试验初期的防护能力大约相当于完好涂层经历6~7次循环试验之后的防护能力,破损部分随着腐蚀周期的变化呈现“钝化—溶解—再钝化—再溶解”的周期性变化规律。     

钛合金紧固件用铝涂层抗电偶腐蚀行为研究

目的研究铝涂层对钛合金紧固件连接铝构件时抗电偶腐蚀的作用。方法采用电偶腐蚀电流、开路电位、极化曲线、电化学交流阻抗等电化学测试技术,分析评价了钛合金紧固件表面用铝涂层的抗电偶腐蚀性能。结果无涂层TC4钛合金和2024铝合金组成的电偶对存在严重的电偶腐蚀;TC4钛合金表面制备铝涂层后,自腐蚀电位从-267 V升高到213 V,表面电阻从771.6Ω升高到2.59×10~8Ω,与2024铝合金组成电偶对的电偶电流密度从80.51μA/cm~2下降到0.45μA/cm~2,其电偶腐蚀等级为B。结论铝涂层可以有效地防止电偶腐蚀。     

直升机旋翼桨叶有机涂层防护性能在户内加速试验中的变化

目的考核评价高原环境下服役的直升机旋翼桨叶典型结构及其防护体系的耐腐蚀性能。方法利用建立的模拟高原环境加速试验谱,再现直升机旋翼桨叶结构防护体系实际服役过程中出现的腐蚀损伤,采取电化学阻抗谱测试研究涂层阻抗的变化。结果经历8个周期的户内加速试验后,新修桨叶试验件表面有机涂层Bode曲线呈现小幅下降,即有机涂层防护性能下降;报废桨叶试验件表面有机涂层的特定频率电化学阻抗模值与原始情况相比仅下降了不到1个数量级。结论报废桨叶试验件表面有机涂层电化学阻抗模值曲线在8个周期后仍然小幅高于未经历户内加速试验的新修桨叶试验件。     

加速腐蚀环境下新型纳米涂层腐蚀行为研究

目的评估新型纳米涂层体系在海洋、工业大气模拟环境下的耐蚀性能。方法采用外观评级法、厚度损失分析法、电化学阻抗分析法、疲劳寿命分析法,对比分析新型纳米涂层体系与TB06-9底漆+TS96-71面漆涂层体系在海洋大气、工业大气模拟环境下不同加速周期的光泽、色差、综合评定等级、厚度损失量、疲劳寿命、阻抗特性。结果随着加速试验加速周期的增加,两类涂层体系综合等级由0级上升至3级、厚度损失量由0μm逐渐增加至15μm、电化学阻抗值下降至10kΩ·cm2,且外部环境谱较内部环境谱、工业大气模拟环境较海洋模拟环境对两类涂层耐蚀性影响较大,但两类涂层体系在各加速谱下作用下,其疲劳寿命循环次数在49000～55000次之间,无明显变化。结论综合分析两类涂层体系腐蚀损伤特性及腐蚀损伤规律,可见纳米涂层具有较好的耐候性,但相比TB06-9底漆+TS96-71面漆涂层体系,其耐蚀性能较差。     

TC21钛合金表面涂层体系在多因素综合加速试验条件下的老化规律研究

目的 研究TC21钛合金表面防护体系(酸洗+环氧底漆+聚氨酯面漆)在多因素协同加速试验条件下的表面性能变化规律。方法 利用一台海洋大气综合模拟试验装置,在户内模拟热带岛礁海洋大气环境,对经历各个加速试验周期后的试样进行外观拍照、光泽度测试、色差测试、光学显微拍照、以及电化学阻抗测试(EIS),并描述相关变化过程。结果 5个周期的加速试验后,试样表面涂层的失光率和色差分别达到45.6%和4.36。涂层在0.01 Hz处的阻抗模值由初始的2.74×10¹⁰ Ω下降为6.21×10⁷ Ω。结论 经历5个周期的户内多因素综合加速试验的过程中,TC21钛合金表面涂层体系的防护效果呈持续下降趋势,但5周期后尚未完全失效。     

某型直升机机体结构关键件涂层耐久性评估

目的 评估某型直升机机体典型结构关键件涂层在内陆温和地区的耐久性,支撑机体总日历寿命延寿工作。方法 对某型直升机大修周期机体结构关键件涂层进行目视检查、涂层光泽度检查和电化学交流阻抗检测,对比分析检测数据,分析机体结构关键件涂层耐久性的影响因素,判定涂层的耐久性。结果 某型直升机机体结构关键件涂层的耐久性较好。失光率检测中,平均失光率为37.8%,整体失光率较小。电化学阻抗检测中,平均电化学阻抗模值为5.58×10⁷ Ω.cm²,未失效,涂层能够有效保护机体结构关键件免于腐蚀环境破坏。结论 大修周期内,某型直升机机体结构关键件涂层的耐久性好,少数区域涂层因光照、磕碰等,耐久性部分程度受到影响,机体结构关键件涂层受温度、湿度、盐雾浓度等的影响较小。     

2种防护涂层体系在湿热海洋环境下防护性能的劣化规律研究

目的 研究2种防护涂层体系在湿热海洋环境下自然暴露3 a的防护性能劣化规律。方法 确定试验件为钢–铝（钢）螺接连接件,试验地点为海南万宁,并按周期测得不同暴露时间下涂层A和涂层B的外观形貌、色差、光泽度、表面傅里叶红外光谱、电化学阻抗的相关数据。通过对比分析测试结果,判断2种涂层在不同暴露时间下的劣化程度,并最终得到其劣化规律。结果 涂层A自然暴露1 a老化严重,紧固件区域涂层剥落,平板区域失光率约为75%,阻抗模量降低5个数量级,色差ΔE~*为5（轻微变色）,涂层有机基团老化降解严重。涂层B自然暴露2 a,老化较严重,紧固件区域涂层剥落、生锈,平板失光率约为20%,阻抗模量降低2个数量级,色差ΔE~*为11（严重变色）,涂层有机基团轻微老化降解。结论 对于螺钉连接结构,连接区域不仅更容易被腐蚀,而且增加了附近平板区域的不一致性。涂层体系B的保护能力优于涂层体系A,涂层体系B的有效保护时间约为2 a,而涂层体系A则不到1 a。     

直升机蒙皮典型结构有机涂层防护性能在模拟高原大气环境中的变化

目的评价服役于高原大气环境中的直升机蒙皮典型结构及其防护体系的防护性能。方法通过模拟高原大气环境加速试验方法再现直升机蒙皮典型结构防护体系实际服役过程中出现的损伤,利用扫描电镜对表面微观形貌进行观察,采用电化学阻抗谱测试研究有机涂层阻抗的变化。结果在实验室加速试验中,蒙皮试验件螺钉周边先出现局部腐蚀,之后腐蚀产物又逐渐减少,而铆钉周边经过多个周期后腐蚀产物都没有显著增多。螺钉中间区域有机涂层电化学阻抗模值直至第8个周期后与原始情况相比才大幅度下降,而铆钉中间区域有机涂层电化学阻抗模值在试验中多次明显下降。结论铆钉周边的有机涂层经过多个周期加速试验仍具有阻挡腐蚀性介质的作用。与螺钉结构的情况相比,铆钉中间区域有机涂层防护性能退化显著。     

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.     

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.     

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.     

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.     

Potential of plant polyphenol oxidases in the decolorization and removal of textile and non-textile dyes

In this study an effort has been made to use plant polyphenol oxidases; potato （Solanum tuberosum） and brinjal （Solanum melongena）, for the treatment of various important dyes used in textile and other industries. The ammonium sulphate fractionated enzyme preparations were used to treat a number of dyes under various experimental conditions. Majority of the treated dyes were maximally decolorized at pH 3.0. Some of the dyes were quickly decolorized whereas others were marginally decolorized. The initial first hour was sufficient for the maximum decolorization of dyes. The rate of decolorization was quite slow on long treatment of dyes. Enhancement in the dye decolorization was noticed on increasing the concentration of enzymes. The complex mixtures of dyes were treated with both preparations of polyphenol oxidases in the buffers of varying pH values. Potato polyphenol oxidase was significantly more effective in decolorizing the dyes to higher extent as compared to the enzyme obtained from brinjal polyphenol oxidase. Decolorization of dyes and their mixtures, followed by the formation of an insoluble precipitate, which could be easily removed simply by centrifugation.     

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.     

Removal of heavy metals from sewage sludge by low costing chemical method and recycling in agriculture

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Isolation and preliminary characterization of a 3-chlorobenzoate degrading bacteria

A study was conducted to compare the diversity of 2-, 3-, and 4-chlorobenzoate degraders in two pristine soils and one contaminated sewage sludge. These samples contained strikingly different populations of mono-chlorobenzoate degraders. Although fewer cultures were isolated in the uncontaminated soils than contaminated one, the ability of microbial populations to mineralize chlorobenzoate was widespread. The 3- and 4-chlorobenzoate degraders were more diverse than the 2-chlorobenzoate degraders. One of the strains isolated from the sewage sludge was obtained. Based on its phenotype, chemotaxonomic properties and 16S rRNA gene, the organism S-7 was classified as Rhodococcus erythropolis. The strain can grow at temperature from 4 to 37℃. It can utilize several （halo）aromatic compounds. Moreover, strain S-7 can grow and use 3-chlorobenzoate as sole carbon source in a temperatures range of 10-30℃ with stoichiometric release of chloride ions. The psychrotolerant ability was significant for bioremediation in low temperature regions. Catechol and chlorocatechol 1,2-dioxygenase activities were present in cell free extracts of the strain, but no （chloro）catechol 2,3- dioxygenase activities was detected. Spectral conversion assays with extracts from R. erythropolis S-7 showed accumulation of a compound with a similar UV spectrum as chloro-cis,cis-muconate from 3-chlorobenzoate. On the basis of these results, we proposed that S-7 degraded 3-chlorobenzoate through the modified ortho-cleave pathway.     

Single and joint effects of pesticides and mercury on soil urease

The influence of two pesticides including chlorimuron-ethyl and furadan and mercury （Hg） on urease activity in 4 soils （meadow burozem and phaeozem） was investigated. The soils were exposed to various concentrations of the two pesticides and Hg individually and simultaneously. Results showed that there was a close relationship between urease activity and organic matter content in soil. Chlorimuron-ethyl and furadan could both activate urease in the 4 soils. The maximum increment of urease activity by chlorimuronethyl was up to 14%-18%. There was almost an equal increase （up to 13%-21%） in the urease activity by furadan. On the contrary, Hg markedly inhibited soil urease activity. A logarithmic equation was used to describe the relationship （P〈0.05） between the concentration of Hg and the activity of soil urease in the 4 tested soils. Semi-effect dose （ED50） values by the stress of Hg based on the inhibition of soil urease in the 4 soils were 88, 5.5, 24 and 20 mg/kg, respectively, according to the calculation of the corresponding equations. The interactive effect of chlorimuron-ethyl or furadan with metal Hg on soil urease was mainly synergic at the highest tested concentrations.