125 resultados para redox chromophore
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Effect of redox cycling on a Ni-YSZ anode prepared from 50 wt.% NiO and 50 wt.% YSZ was investigated by using temperature-programmed reduction (TPR), XRD and SEM techniques. XRD results showed that NiO was formed during re-oxidation. Both the XRD and TPR results depicted that the conversion of nickel to NiO depended on the re-oxidation temperature. The oxidation of Ni to NiO occurred quickly in the initial several minutes and then reached a quasi equilibrium. The TPR profiles tracing the redox cycling showed that it brought continuous changes in the NiO micro-structure at 800 degrees C, whereas at 600 degrees C it had only little effects on the reduction of NiO. Re-oxidation resulted in the formation of spongy aggregates of NiO crystallites. Redox cycling at 800 degrees C led to a continuous decrease in the primary crystallite size of NiO and a high dispersion of the Ni particles. A continuous expansion of the slice sample was observed in both of the oxidized and reduced states during the redox cycling at 800 degrees C, whereas this process did not occur during the redox cycling at 600 degrees C. (c) 2005 Elsevier B.V All rights reserved.
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The optical loss coefficient at 1053-nm wavelength, influenced by Fe ions in N31-type Nd-doped phosphate laser glass, was determined precisely and analyzed in detail. It is found that the optical loss coefficient per unit of Fe concentration (cm^(-1)/ppmw) increases with Fe concentration in the range of 0---300 ppmw, but it approaches a constant as the Fe concentration is larger than 300 ppmw. Such a concentration effect is due to a shift in the redox equilibrium between Fe3+ and Fe2+ ions in the glass. The effect of oxygen pressure, temperature, and variable valence states of other metal ions in glass samples on the optical loss is also discussed.
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Bismuth (Bi)-doped and Bi/Dy co-doped chalcohalide glasses are investigated as promising materials for amplifiers in optical communication. The samples synthesized at lower melting temperatures (MTs) are characterized by more intensified infrared emissions. With respect to the redox process of a liquid mixture at different MTs, we attribute an emission at 1230 nm to low-valent Bi ions. The lower MT favors the formation of LVB ions, i.e. Bi+ or Bi2+, while the higher MT promotes the production of higher-valent Bi ions Bi3+. An enhanced broadband infrared luminescence with the full-width at half-maximum over 200 nm is achieved from the present Bi/Dy co-doped chalcohalide glasses.
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The doped Eu3+ ions can be partly reduced to Eu2+ in a series of MO-B2O3: Eu (M=Ba, Sr, Ca) glasses synthesized in air atmosphere, but not in the 12CaO-7Al(2)O(3): Eu glass. The different redox-behavior of Eu ions in these two glass systems is attributed to the different host optical basicity. It is found that a lower valence state of Eu2+ is more favorable in acidic glasses, which have lower optical basicities. A notion of the critical value of optical basicity is introduced empirically, which can be used as a guide for the selection of glass composition suitable to incorporate Eu2+ for luminescence. (C) 2006 Elsevier B.V. All rights reserved.
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National Nature Science Foundation of China (Grant No. 60607015)
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籽粒的灌浆是将光合器官合成的有机物贮存在籽粒中的过程。这一过程直接决定了籽粒的产量及品质。先前研究表明灌浆籽粒中贮存物质的累积是各种代谢活动和细胞学过程协同作用的结果,但灌浆的分子机制目前还不是非常清楚。水稻是研究籽粒灌浆的优良模式材料,不仅因为它是世界上最重要的淀粉食物来源,更重要的是其全基因组的测序完成为分子机制的研究带来极大的便利。我们对发育水稻籽粒的观察表明在开花后6 天,籽粒就已完成了胚的分化和胚乳的细胞化;此后籽粒经历了一个显著的细胞增大过程,并在开花后12 天左右达到成熟籽粒的大小;而籽粒的灌浆过程起始于开花后6 天,这个过程一直持续到开花后20 天。因此,我们将开花后6 天到20 天的籽粒分为8 个连续的发育阶段进行动态的蛋白质组分析,396个蛋白点的表达在灌浆过程中发生了两倍以上变化。质谱鉴定得到的345 个差异表达的蛋白划分为10 个不同的功能类别。其中新陈代谢类(45%)和蛋白合成/终点(destination)类(20%)两个功能类别中就包括了大多数的差异表达蛋白,预示着这两类蛋白在籽粒发育中的重要性。蛋白功能群的表达分析显示与淀粉合成和乙醇发酵相关的蛋白在发育过程中大幅度的上调,而与碳代谢中心过程(糖酵解和三羧酸循环)相关蛋白呈现明显的下调趋势。大多数的功能类或(亚类)也呈现出下调的表达趋势,如细胞生长/分裂类,蛋白合成类,水解类,信号传导类和转录类。蛋白表达分析的结果表明蛋白的表达随籽粒的发育发生了显著的变化,这些变化与籽粒在不同阶段的发育和代谢过程密切相关并协调一致,是细胞从生长分裂过渡到以淀粉合成为中心的物质基础。同时也说明代谢重点由中心碳代谢向乙醇发酵的转变对于籽粒的发育和淀粉的合成与累积具有重要意义。 籽粒发育的研究表明在长到成熟籽粒大小后(开花后12 天),籽粒的代谢集中到淀粉累积途径上,一直持续到进入脱水期(18 天),绝大多数淀粉合成相关蛋白在这期间到达表达的顶点。为了解淀粉累积关键时期淀粉合成关键部位(胚乳)的发育规律,我们进一步应用DIGE 技术对这一淀粉累积关键时期(灌浆中后期,开花后12 到18 天)的蛋白表达特性进行分析。细胞学的观察发现胚乳在灌浆后期先后经历了过氧化氢的爆发、半透明胚乳的形成以及胚乳细胞死亡事件。相应的DIGE 分析显示有321 个蛋白点在胚乳的后期发育中发生了显著的表达变化。细胞学的观察结合DIGE 分析显示胚乳的后期发育是一个典型的衰老过程:细胞结构的崩溃;氧化自由基的爆发;脱水干燥;蛋白、脂类和DNA 由同化作用向异化作用的代谢转化。与代谢转化相伴随的细胞营养的重新分配是胚乳后期发育的一个显著过程。DIGE分析全面展示了参与营养重新分配相关蛋白在后期发育中的表达变化,为细胞学中观察到的有机物向淀粉的转化提供了清晰的蛋白水平的证据支持。在鉴定的差异表达蛋白中有2/3 的蛋白是已知的对氧化电位变化敏感的蛋白,表明由H2O2 爆发形成的氧化压力将引起氧化还原调控从而对胚乳的后期发育进行全面的影响。而其中与碳元素代谢相关的代谢途径中尤其富含氧化还原电位敏感的蛋白,表明后期的营养重新分配以及淀粉的累积受到氧化还原电位的紧密调控。另一方面,H2O2 的爆发激发了胚乳中的抗氧化体系。由抗氧化蛋白(如thioredoxin、抗坏血酸和超氧化物歧化酶等)、氧化还原敏感蛋白、代谢中间产物以及glyoxalase 构成的抗氧化体系在胚乳后期发育中协同作用调节氧化还原电位的变化,从而控制胚乳细胞衰老的节奏。另外,我们发现与RraA 相关的转录本的调控在胚乳发育末期急剧上调,在调控的代谢途径、调控时间以及调控的部位与氧化还原调控相重叠,并且支持RraA 活动有利于胚乳细胞对氧化压力的适应。所有这些结果表明内生的过氧化氢(或氧化自由基)在胚乳的后期发育和淀粉累积中起到核心的调控作用。
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植物已经演化出多种保护其免受强光抑制和破坏的机制,从而使植物体在自然界能够应付复杂多变的光照环境。虽然人们早就确定Cyt b-559存在于PSII反应中心内,但目前对其性质与功能的认识还不充分。本工作的目的就是研究Cyt b-559天然分子特性,探讨其生理功能和存在的意义。取得了一些有新意的结果: 1、依据PSII反应中心分离纯化的原理,应用更有效的层析介质DEAE-Sephacel,我们设计了快速高效的从菠菜和水稻中分离纯化Cyt b-559的方法和流程,获得了高纯度的样品。它们在非变性胶电泳中具有相同的泳动性。蛋白组分的HPLC结果证明,纯化的Cyt b-559的确由两个亚基组成,α亚基和β亚基的分子量用我们设计的适合于分析小蛋白的Tricine—SDS—PAGE方法准确测定为9.4kDa和4.5kDa。 2、利用HPLC技术分析了纯化的Cyt b-559样品的色素组成,结果表明Cytb-559中含有Chl α而不含类胡萝卜素分子,这一结果通过吸收光谱和共振拉曼光谱的分析得到进一步地证明。通过等电聚焦方法分析了Cyt b-559的等电点,发现其亚基的等电点相差很大,全蛋白的等电点与...更多D1、D2蛋白的等电点也不相同,推测在体内生理pH条件下它们具有相反带电性而在PSII组装中发挥作用。 3、低温荧光光谱的检测结果表明,Cyt b-559的荧光发射峰位在563nm和666nm;首次证明Cyt b-559可以发出荧光和将电子传递给结合在其上的辅助叶绿素,但传递能力比较低故而导致其荧光特性与PSII反应中心的不相同。Cytb-559的紫外荧光光谱表明Trp残基位于其内部的疏水区域,证明Cyt b-559中的芳香族氨基酸可能在其功能的发挥中起一定作用。 4、通过MCD的分析,发现Cyt b-559中血红素的MCD信号在540—580nm和400—440nm波段,而且光谱形状和强度与PSII反应中心的相一致,说明PSII反应中心该范围内的MCD信号中有Cyt b-559的贡献。FTIR光谱的测定结果证明Cyt b-559血红素的配体是组氨酸,其二级结构中α-螺旋占了一半。此外,还比较了Cyt b-559和PSII反应中心的膜脂成分,发现两者有很大的相似性。不同植物来源的Cyt b-559在许多性质上都表现出高度一致,从一个侧面证明Cyt b-559在进化中的保守性。 5、PSll反应中心发生光破坏时,原初电子供体P680己受到严重破坏。我们发现,在光抑制的最初一段时间内,Cyt b-559吸收峰值发生变化:在受体侧光抑制的条件下,其吸收峰值先略有增加而后才下降,而在供体侧光抑制条件下则相反,说明 Cyt b-559对光抑制的发生非常敏感,可能在光抑制早期保护PSll反应中心。 6、纯化的Cyt b-559的组氨酸含量在照光前后没有显著的变化,说明 PSll反应中心内被破坏的组氨酸不属于Cyt b-559。PSll反应中心所含的组氨酸中有些可被DEPC修饰,但我们的实验结果表明DEPC不能修饰Cyt b-559的组氨酸。这可能有利于Cyt b-559保护功能的发挥。 7、我们观察到,在两种光抑制条件下,LP Cyt b-559光还原和 HP Cyt b-559光氧化具有对pH值的依赖性,说明Cyt b-559在光保护中的作用不仅与其高低电势态有关,而且与其质子化程度有联系。CCCP促进HP Cyt -559释放质子,从而维持循环电子传递。DCBQ和 DCMU在很低浓度时都抑制 Cyt b-559光还原,前者不影响Cyt b-559光氧化而后者在CCCP存在时也会抑制Cyt b-559光氧化。 8、Cyt b-559有定位PSll反应中心其它蛋白的锚蛋白的作用。黄化苗转绿实验证明在 HP Cyt b-559的含量增加超过 45%以后放氧活性开始逐渐增加。Cytb-559从低电势态到高电势态的转变是放氧复合物组装到PSll反应中心的关键步骤之一。在植物正常生长时,Cyt b-559与 P680的其它电于供体发生竟争,起到安全阀门的作用。 9、在逆境条件下,Cyt b-559具有保护PSll反应中心免受强光破坏而起到“分于开关”的作用。我们的实验表明,在室温条件下存在通过Cyt b-559的环式电子流,存在从氧化态LP Cyt b-559到还原态HP Cyt b-559的一个循环,其中的氧化还原变化与质子化/去质子化反应相连。通过与其它血红素蛋白的比较,我们推测 Cyt b-559“分子开关”的关键是:光抑制情况下,铁原子与远端His之间的疏水空穴被氧自由基占据后使得铁进入叶琳中央孔中,迫使近端HIS向叶琳平面位移,从而引起 Cyt b-559构象改变,使电势态发生转变。
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本文由两部分组成,一部分是关于一组新型除草剂(K-15,K-23)的抑制特性及作用位点的研究;另一部分是关于碳酸氢盐对细胞色素b-559高电势的保护作用的研究。 在第一部分,我们首先研究了抑制剂K-23对Psn放氧活性、DCIP光还原和可变荧光等光合特性的影响。研究发现,K-23在低浓度时刺激放氧活性,而在相对高浓度时抑制放氧活性。但是,K-23在低浓度时却有效地抑制了可变荧光。这些数据表明了新型抑制剂的抑制反应是基于氧化还原作用而不是猝灭作用。此外,通过采用胰蛋白酶消化类囊体膜的方式初步检测了新型抑制剂的作用部位,其结果表明:虽然新型抑制剂抑制受体侧电子传递,但它的抑制部位与DCMU不同。 其次,研究了新型抑制剂对光系统II色素蛋白复合体与多肽组分的影响及抑制剂的键合蛋白。应用SDS-PAGE技术,发现新型抑制剂主要作用于光系统II的反应中心蛋白。用温和的Deriphat-PAGE分析也证实了新型抑制剂作用于核心复合物,导致核心复合物二聚体消失。 进一步用SDS-PAGE分析新型抑制剂对Psn多肽组分的影响,发现新型抑制剂主要影响D.、D2、CP43和CP47。用荧光发射的方法确定了K-15键合在D2蛋白上。 最后,结合荧光动力学和HPLC方法,分别从定性和定量的角度,以核心复合物以及抑制剂存在下从BBY中分离的核心复合物为研究对象,详细研究了抑制剂对QA的取代作用。研究发现,在无去垢剂或低浓度去垢剂存在情况下,由于不能创造出适合于QA存在的疏水环境,我们没有得到QA被K-15取代的实验证据。而在抑制剂K-15存在下,用2.2% HTG从BBY分离的核心复合物的实验中,检测不到正的可变荧光Fv,而是得到了降低的FM,这个结果表明QA已被抑制剂在它的作用位点处所取代。 在第二部分,研究了pH5.0—7.0范围内碳酸氢盐对Cyt b-559氧化还原状态转变的影响。首先研究了pH5.0~7.0条件下碳酸氢盐对PSII Cyt b-559还原减氧化差异吸收光谱的影响,发现铁氰化钾还原的PSII Cyt b-559 HP的含量随介质pH值的降低而减少。然而,碳酸氢盐的加入阻止了由于介质pH降低而引起的Cyt b-559由高电势向低电势的转化。比如,当样品温育在pH5.0的介质中,铁氰化钾还原的Cyt b-559 HP含量占总量的25%-30%,当介质中加入2mmol/L碳酸氢盐后Cyt b-559 HP的含量上升,占总量的50%-56%。碳酸氢盐效应对氢醌还原的Cyt b-559HP含量的影响尤为显著。pH6.5时碳酸氢盐对Cyt b-559的还原氧化状态的影响不显著。其次,分别研究了PSII经Tris处理去除锰簇和三个外周蛋白及NH20H处理去除锰簇和17 kDa和23 kDa后,碳酸氢盐对Cytb一559 HP影响的pH依赖值,发现不论在pH5.0还是pH6.5的介质中碳酸氢盐效应都不存在。 综合以上实验结果,我们认为碳酸氢盐对酸化引起的Cyt b-559氧化还原状态的影响与它和锰的作用有关,但也不能排除钙离子与碳酸氢盐之间的协同作用。
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Microorganisms play an important role in removing pollutants from constructed wetlands. We investigated the microbial characteristics in a novel integrated vertical-flow constructed wetland (IVCW), which has been in operation in Wuhan, China since 1998. We used phospholipid fatty acid (PLFA) and amoA gene to analyze the structure and diversity of the microbial community within the IVCW. PLFA results suggested that the amount of bacterial PLFA was significantly higher than that of fungal PLFA, but the total microbial biomass represented by PLFA index was low in the system. Microbial spatial distribution showed significantly higher bacterial (both G(+) and G(-)) and fungal biomass in the surface than in the subsurface layers. The ratios of monounsaturated to branched PLFA demonstrated that an anaerobic layer sandwiched by two aerobic layers existed in the IVCW, consistent with the redox potential results. Analysis of the amoA revealed the presence of Nitrosomonas-like sequences in the surface substrate of the downflow chamber and apparent diversities of ammonia-oxidizing bacteria in the system. These results suggest that microorganisms, despite their relatively low biomass, have inhabited the IVCW, and the results will offer some valuable information on microbe to system designers and managers.
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A fluorescence immunoassay for human IgG (Ag) was developed using a pH-sensitive polymer prepared by thermal initiation or redox initiation polymerization as a carrier. In the competitive immunoassay, appropriate quantity of Ag was immobilized on the polymer and the standard Ag (or sample) solution, and a constant amount of fluorescein isothiocyanate labeled goat anti-human IgG antibody (Ab-FITC) was added. Immobilized Ag and the standard (or sample) Ag competed for binding to the Ab-FITC in 37 C in homogeneous format. After changing the pH to separate the polymer-immune complex precipitate, it was re-dissolved and determined by fluorescence method. The results showed that the immobilization efficiency, immunological reaction activities of immobilized Au and phase transition pH range were improved as Ag was immobilized by thermal initiation instead of redox initiation polymerization. Under optimum conditions, the calibration graphs for the Ag in both methods, thermal initiation and redox initiation, were linear over the concentration range of 0.0-1000 ng mL(-1), with detection limits 8 (thermal initiation) and 12 ng mL(1) (redox initiation), respectively. Moreover, some pH-sensitive polymer prepared only in organic solvent or under high temperature could also be used as an immunoreaction carrier by thermal initiation polymerization. Thermal initiation polymerization was a better immobilization mode. (C) 2004 Elsevier B.V. All rights reserved.
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Goal, Scope and Background. In some cases, soil, water and food are heavily polluted by heavy metals in China. To use plants to remediate heavy metal pollution would be an effective technique in pollution control. The accumulation of heavy metals in plants and the role of plants in removing pollutants should be understood in order to implement phytoremediation, which makes use of plants to extract, transfer and stabilize heavy metals from soil and water. Methods. The information has been compiled from Chinese publications stemming mostly from the last decade, to show the research results on heavy metals in plants and the role of plants in controlling heavy metal pollution, and to provide a general outlook of phytoremediation in China. Related references from scientific journals and university journals are searched and summarized in sections concerning the accumulation of heavy metals in plants, plants for heavy metal purification and phytoremediation techniques. Results and Discussion. Plants can take up heavy metals by their roots, or even via their stems and leaves, and accumulate them in their organs. Plants take up elements selectively. Accumulation and distribution of heavy metals in the plant depends on the plant species, element species, chemical and bioavailiability, redox, pH, cation exchange capacity, dissolved oxygen, temperature and secretion of roots. Plants are employed in the decontamination of heavy metals from polluted water and have demonstrated high performances in treating mineral tailing water and industrial effluents. The purification capacity of heavy metals by plants are affected by several factors, such as the concentration of the heavy metals, species of elements, plant species, exposure duration, temperature and pH. Conclusions. Phytoremediation, which makes use of vegetation to remove, detoxify, or stabilize persistent pollutants, is a green and environmentally-friendly tool for cleaning polluted soil and water. The advantage of high biomass productive and easy disposal makes plants most useful to remediate heavy metals on site. Recommendations and Outlook. Based on knowledge of the heavy metal accumulation in plants, it is possible to select those species of crops and pasturage herbs, which accumulate fewer heavy metals, for food cultivation and fodder for animals; and to select those hyperaccumulation species for extracting heavy metals from soil and water. Studies on the mechanisms and application of hyperaccumulation are necessary in China for developing phytoremediation.