72 resultados para CU3(OH)2(CO3)2


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The interfacial tension is measured for Cyanex 302 in heptane and adsorption parameters are calculated according to Gibbs equation and Szyskowski isotherm. The results indicate that Cyanex 302 has a high interfacial activity, allowing easy extraction reaction to take place at the liquid-liquid interface. The extraction kinetics of yttrium(III) with Cyanex 302 in heptane are investigated by a constant interfacial cell with laminar flow. The effects of stirring rate, temperature and specific interfacial area on the extraction rate are discussed. The results suggest that the extraction kinetics is a mixed regime with film diffusion and an aqueous one-step chemical reaction proposed to be the rate-controlling step. Assuming the mass transfer process can be formally treated as a pseudo-first-order reversible reaction with respect to the metal cation, the rate equation for the extraction reaction of yttrium(III) with Cyanex 302 at pH <5 is obtained as follows:R-f = 10(-7.85)[Y(OH)(2)(+)]((a))[H(2)A(2)]((o))(1.00)[H+]((a))(-1.00)Diffusion parameters and rate constants are calculated through approximate solutions of the flux equation.

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The stability constants and species distributions of complexes of two lanthanide ions, Eu (III) and Tb(III), with a macrocyclic ligand, 3,6, 9, 17 20, 23-hexaazo-29, 30-dihydroxy-13, 27-dimethyl-tricylco-[23,3,1,1(11,15)] triaconta-1 (28) 11,13,15 (30), 25 26-hexane (BDBPH), in 1: 1 and 2: 1 system, were determined potentiometrically in 50% ethanol solution, at 35.0 degrees C and I = 0.100 mol/L (KCl). The two metal ions could form deprotonated mono- or dinuclear complexes with BDBPH with high stability after the three protons of the ligand completely neutralized. At higher pH values, Eu(M) could not form hydroxo complexes with BDBPH, while Tb(III) could form hydroxo complexes in the types of M2L(OH) M2L(OH)(2) and M2L (OH)(2). The kinetic study on the hydrolysis reaction of his (4-nitrophenyl) phosphate (BNPP) catalyzed by Tb-BDBPH system (2:1) was carried out in aqueous solution (pH 7.0 similar to 10.0) at 35 degrees C with I = 0.1000 mol/L (KCl). The second-order rate constant k(BNPP) (2.3 x 10(-3) (mol/L)(-1)center dot s(-1)) was determined. The dinuclear monohydroxo species, L-Tb-2-OH, is kinetically active species.

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目前使用的碱性二次电池中,镍系列电池占有很重要的地位,其中镍电极是其核心.镍电极的研究集中于掺杂离子对电极过程的作用机理、具有优良的电化学性能的稳定的α-Ni(OH)2和纳米Ni(OH)2的制备等三个热点上.由于NiOOH/Ni(OH)2电化学储能所涉及的活性物质在碱性介质中具有不溶解性及长寿命的优点,所以氢氧化镍特别适宜作为碱性蓄电池的正极活性物质.

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The behaviour of the electroplated copper film electrode on tin oxide/glass or glassy carbon surface was studied in potassium hydroxide medium by cyclic voltammetry and in situ transmission spectroelectrochemistry. The results indicate that the electroplated copper film electrode is similar to a copper electrode and cyclic voltammetry with this electrode affords more resolution. The anodic peaks were found to correspond successively to the adsorption of oxygen, the formation of a surface layer of Cu2O, the formation of a surface layer of Cu(OH)2 or CuO and formation of a thick multilayer film of CuO. This is the first time it has been proposed that a surface layer of Cu(OH)2 or CuO is formed from the oxidation of the surface layer of Cu2O. Similarly, a clear interpretation is presented that the cathodic peaks correspond successively to the reduction of CuO to Cu2O, the reductions of Cu2O to Cu and the soluble Cu(II) species to Cu. On the other hand, a shoulder peak related to the chemical transformation of Cu(OH)2 to CuO was first observed.

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铜管一直是电厂凝汽器的主要应用管材,但由于其抗冲刷和抵御污染物腐蚀的能力差,特别不耐氨蚀,美国和欧洲大量使用不锈钢管替代铜管作为冷凝管,然而不锈钢管在我国的运用仅处于初步阶段。 常使用锌、铝阳极对铜管进行牺牲阳极保护,然而存在着电位差过大、阳极溶解过快的问题。铁基牺牲阳极与铜电位差适当、来源广泛、价格便宜,在一些工程上有所应用,但是目前针对铁基牺牲阳极的理论研究报道很少。 本文选用紫铜管、304不锈钢管作为实验用管材,首先运用实验室全浸实验、极化曲线和电化学阻抗研究了二者在海水和淡水中的腐蚀性能以及CO2、溶解氧对其腐蚀的影响。结果表明:CO2会加速二者的腐蚀,溶解氧却对它们的腐蚀影响不同,促进铜管的腐蚀却抑制不锈钢管的腐蚀;随浸泡时间的延长,紫铜管由于表面产物膜的生成耐蚀性提高,304不锈钢管的耐蚀性却降低;淡水中,304不锈钢管和紫铜管都具有很好的耐蚀性能。随后,运用失重法和极化曲线对比研究了紫铜管、304不锈钢管的氨蚀性能,运用SEM分析和电化学阻抗研究了紫铜在不同浓度氨溶液中的腐蚀机理。发现,304不锈钢管的耐氨蚀能力远远好于铜管;溶解氧是影响氨蚀的关键因素,其对二者氨蚀的影响也不同;紫铜管在低氨浓度和高氨浓度溶液中腐蚀机理和产物不同,低氨浓度时形成保护性的产物膜(CuO 和Cu(OH)2),高氨浓度时由活化溶解控制,生成可溶的[Cu (NH3)4]2+。 选用工业纯铁、35钢为牺牲阳极材料。恒电流实验结果表明它们具有良好的牺牲阳极性能;通过极化曲线和自腐蚀电位测试分析,认为将二者用于铜管牺牲阳极保护是可行的;实验室阴极保护效果测试表明,工业纯铁和35钢对紫铜管具有良好的保护效果,保护度达90%以上。

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在海水环境中,溶解氧阴极还原反应是钢铁材料腐蚀的主要因素之一,海水中的氯离子(Cl−)和硫酸盐还原菌(SRB)可能对溶解氧还原反应发生作用从而影响钢铁材料的腐蚀行为。本文以海洋工程材料Q235钢作为研究对象,通过循环伏安法、电化学阻抗谱、旋转圆盘电极和旋转圆盘-圆环电极线性扫描伏安法等电化学方法,研究了Cl−和硫酸盐还原菌对Q235钢电极表面溶解氧还原反应的影响,并对其影响机制进行了探讨。 研究表明:Q235钢在模拟混凝土孔隙液中电极表面氧化物的还原反应和溶解氧的还原反应同时进行;溶解氧还原反应在阴极反应电位范围内最初为混合过程控制的二电子反应,电位较负时为扩散过程控制的四电子反应。当在0.02 M Ca(OH)2溶液中加入Cl−时,随着Cl−浓度的增加,溶液电阻减小,溶解氧还原反应峰电位逐渐正移,即溶解氧还原反应的过电位减小;同时随着氯离子浓度的增加溶解氧还原反应速率逐渐减小。 由于硫酸盐还原菌在电极表面形成的生物膜阻碍了溶解氧到达电极表面,使得溶解氧还原反应与无菌时相比在一定程度上受到抑制,溶解氧还原反应速率降低;同时由于硫酸盐还原菌形成生物膜的作用,使得溶解氧还原机理也发生了改变,在没有硫酸盐还原菌时溶解氧还原以四电子还原为主,当硫酸盐还原菌数量较少时,溶解氧还原反应以二电子反应主,当硫酸盐还原菌数量较多时转为一电子反应为主。

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Marine sediment is the important sources and sinks of carbon. The inorganic carbon(IC) in marine sediments plays an important role in carbon cycling. In order to understand IC function in carbon cycling, sequential extraction method based on IC combined chemical strength difference were established to get five phases: NaCl phase (step I), NH3 - H2O phase (step II), NaOH phase (step III), NH2OH . HCl phase (step IV) and HCl phase(step V). The best extraction conditions were obtained by a series of experiments. Extractants were added into plastic centrifuge tubes in Step I - M, the capped tube were placed on a shaker table to keep the solids suspended for two hours. The suspended solution was separated by centrifugal, the residues were washed with water. The two supernatant were combined and the CO, was finally determined by volumetric analysis. The residues were transferred into conical flask in step IV and V, and then the extractants were added. The produced CO2 was adsorbed by saturated Ba(OH)(2) solution, and determined by volumetric analysis. This method for IC has a good precision in the analysis sediment samples.

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Cyclic voltammetry, electrochemical impedance spectroscopy, and rotating disk electrode voltammetry have been used to study the effect of chloride ions on the dissolved oxygen reduction reaction (ORR) on Q235 carbon steel electrode in a 0.02 M calcium hydroxide (Ca(OH)(2)) solutions imitating the liquid phase in concrete pores. The results indicate that the cathodic process on Q235 carbon steel electrode in oxygen-saturated 0.02 M Ca(OH)(2) with different concentrations of chloride ions contain three reactions except hydrogen evolution: dissolved oxygen reduction, the reduction of Fe(III) to Fe(II), and then the reduction of Fe(II) to Fe. The peak potential of ORR shifts to the positive direction as the chloride ion concentration increases. The oxygen molecule adsorption can be inhibited by the chloride ion adsorption, and the rate of ORR decreases as the concentration of chloride ions increases. The mechanism of ORR is changed from 2e(-) and 4e(-) reactions, occurring simultaneously, to quietly 4e(-) reaction with the increasing chloride ion concentration.

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目的对比分析国家一类动物药塞隆骨和禁用传统中药材虎骨中的19种矿物质元素的含量.方法骨骼样品经灰化或消解处理后,采用原子吸收光谱法、氢化物原子荧光光谱法、催化极谱法等分析方法测定矿物质元素.结果两种动物骨骼中元素含量差异显著,塞隆骨11种元素高于虎骨,特别是Cu、Zn、Fe、Mn、Se等生命活动必需微量元素塞隆骨极为显著地高于虎骨,而组成骨骼的主要成分Ca、P则为虎骨高于塞隆骨.矿物质元素在头骨、脊梁骨和腿骨中分布非常不平衡,多数元素以头骨中分布最为丰富,而5种常量元素Ca,P,Na,Mg,K的含量为腿骨>头骨>脊梁骨.骨骼中主要成分Ca和P的存在形式主要为羟磷灰石Ca10(PO4)6(OH)2.结论塞隆骨骨骼中的矿物质元素与虎骨有可比性,必需微量元素塞隆骨明显优于虎骨.

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近些年来,利用海洋生物碳酸盐硼同位素重建古海水pH,计算当时大气CO2含量,进而推测古气候的变化已成为国际同位素地球化学界研究的热点问题,被称为δ11B-pH技术。古海水的δ11Bsw是否恒定、B(OH)4−和B(OH)3间理论的硼同位素分馏系数4/3是多少以及碳酸盐的δ11Bcarb是否等于海水B(OH)4−的δ11B4值是该技术成功的三个关键。但到目前为止以上三项问题还没得到完全证实。 为确定方解石的硼同位素组成与海水pH的依赖关系,已进行过大量实验研究。他们的结果与预期的假设一致,支持了B(OH)4-是掺入方解石结构主要形式的假设。但近期 Pagani(2005)指出B(OH)4-也许不是掺入方解石结构的主要形式,B(OH)3也可能同时掺入进碳酸盐。肖应凯等(2006)的无机碳酸盐沉积实验发现碳酸盐沉积和母液间的硼同位素分馏系数大于1的异常现象,认为碳酸钙中镁或其它微量元素的存在是重要原因,推断这是在高pH生成Mg(OH)2沉积后11B优先掺入的缘故,推断有B(OH)3掺入碳酸盐的可能。 以前进行的沉积实验,只考虑到碳酸钙本身,确实证明了硼只以或主要以B(OH)4-参与进生物碳酸钙。但天然的海洋生物碳酸盐含有镁、锶、铁等微量元素,这些微量元素的存在可能会改变硼的参与行为,从而对硼同位素分馏产生影响。现代珊瑚礁中水镁石普遍存在,这是否会影响珊瑚的硼同位素组成而导致δ11B-pH技术的误差还值得研究。 针对以上问题,主要对硼掺入进Mg(OH)2的形式及分馏机理,现代珊瑚中镁、锶等微量元素与硼浓度及硼同位素的关系进行研究,并用生物碳酸盐的硼同位素对陆相产出有孔虫的沉积环境进行判别。 通过研究,得到以下几点认识: 1. 在Mg(OH)2从pH9.5~13的含硼合成海水中沉积时,Mg(OH)2沉积11B的变化范围为-1.20‰~28.26‰,高于合成海水的11B (-7.00±0.07‰),沉积和海水间的硼同位素分馏系数固/液变化范围为1.0177~1.0569,平均值为1.0329,这是H3BO3优先掺入的结果,造成11B在Mg(OH)2沉积中富集。 2. Mg(OH)2沉积的硼浓度和硼在Mg(OH)2沉积与滤液间的分配系数Kd的变化范围分别为228.61 g/g~937.79 g/g和9.31~494.20。高pH值时硼掺入Mg(OH)2的过程中吸附作用占有重要位置。 3. Mg(OH)2吸附实验表明,硼掺入Mg(OH)2非常迅速,4 h能达到平衡。平衡后Mg(OH)2中硼浓度[B]固和固相与溶液相间的分配系数Kd随pH设定的升高和固液比的降低而降低。而且最高的[B]固和Kd均远高于硼被金属氧化物或粘土矿物吸附时的对应值,表硼具有很强的掺入Mg(OH)2的能力。 4. 吸附平衡时溶液相的11B液f (-19.2‰~-17.8‰)均低于原始溶液的11B液i (-7.00±0.07‰),计算的Mg(OH)2与平衡溶液间的硼同位素分馏系数固-液变化范围为1.0186~1.0220,平均值为1.0203。这充分表明,硼掺入Mg(OH)2时11B优先进入固相,这是B(OH)3优先掺入的结果。 5. 硼以B(OH)3和B(OH)4-两种形式同时掺入Mg(OH)2,并以B(OH)3优先掺入为主,pH设定越低掺入的B(OH)3比例越高。 6. 硼将通过吸附和与Mg(OH)2的沉淀反应而掺入Mg(OH)2,两者共同决定了Mg(OH)2中硼同位素分馏特征。 7. Ca、Sr、B和Na在珊瑚中均得到富集,而Mg在珊瑚中却是贫化的。珊瑚的B浓度主要不是由这几种元素决定的。 8. 珊瑚δ11Bcarb的变化范围为22.8‰~27.9‰,平均为25.2‰。除与B浓度相关性明显外,珊瑚δ11Bcarb与其它四种元素的相关性不强。北海涠洲岛、灯楼角和三亚三地珊瑚与海水间的分馏系数carb-sw分别为0.9839、0.9847和0.9850。珊瑚与海水B(OH)3间的分馏系数carb-3的变化范围为0.9772~0.9800,平均值为0.9788,随pH升高carb-3减小。珊瑚的平均δ11Bcarb基本位于采用=0.9772时理论计算的δ11B4曲线之上,而且都低于原始合成海水的δ11Bcarb,表明硼是以B(OH)3和B(OH)4-两种形式同时掺入进珊瑚中的,并以B(OH)4-优先掺入为主。 9. 由于B(OH)4- 和B(OH)3同时进入到珊瑚中,d11Bcarb=d11B4的假设不能成立,由所测定生物碳酸盐的δ11Bcarb值计算的海水pH值会产生误差,使δ11B-pH技术变得更为复杂。 10. 实验模拟与自然的真实情况是有差距的,不能完全用实验模拟来代替自然的真实情况。 11.杨户庄剖面的第四纪早期有孔虫的生存环境是非海相环境,不是“海侵”或“海泛”的结果;同时也表明有孔虫并非是特有的海洋生物,它完全可以在陆相环境中存在。

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用光学多道分析仪(OMA光学系统)测量了氢氧燃烧驱动激波管中典型状态下正激波后高温空气不同时刻的瞬态光谱。光谱结果显示高温空气的光谱中有很强的OHA2∑+─X2∏光谱。通过采用线线合成光谱的方法得到激波后不同时刻高温空气中OH分子的转动温度。

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Monodisperse hexagonal Ln(OH)(3) (Ln = Eu, Sm) submicrospindles with uniform morphology and size have been Successfully synthesized in a large scale via a Facile aqueous solution route from the mixture of aqueous solutions or LnCl(3) and NaOH at 5 degrees C without using any surfactant or template. The as-synthesized products are characterized by X-ray diffraction (XRD), thermogravimetric analysis (TGA), energy-dispersive X-ray (EDX) spectra, scanning electron microscopy (SEM), transmission electron microscopy (TEM), and high-resolution transmission electron microscopy (HRTEM). The SEM and TEM images show that the as-formed Ln(OH)(3) samples have a spindlelike shape with an equatorial diameter of 80-200 nm and a length of 500-900 nm, which are aggregates of even smaller nanoparticles.

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The crystal structures of EtEDTB.1.4C(2)H(5)OH.5H(2)O 1 and H4EtEDTB(ClO4)(4).C2H5OH 2 (EtEDTB = N, N,N',N'-tetrakis[2-(1-ethylbenzimidazolyl)methyl]-1,2-ethanediamine) have been determined by single-crystal X-ray diffraction method. Compound 1 crystallizes in the space group P(1) over bar with a = 11.489(2), b = 11.866(3), c = 12.002(3) Angstrom, alpha = 97.47(2), beta = 114.564(13), gamma = 114.11(2)degrees, V = 1266.6(5) Angstrom(3), Z = 1, M-r = 847.48, D-c = 1.111 g/cm(3), F(000) = 456 and mu(MoKalpha) = 0.076 mm(-1). A total of 5207 reflections were measured for 1, of which 4323 were independent. The structure of 1 was solved by direct methods and refined by full-matrix least-squares technique to the final R = 0.0706 and wR = 0.1802 for 1318 observed reflections with I > 2sigma(I). In the structure of 1, centrosymmetric EtEDTB molecules are linked by hydrogen bonds through water and ethanol to form 2-dimensional network. Compound 2 crystallizes in the space group C2/c with a = 24.260(5), b = 13.040(3), c = 17.680(4) Angstrom, beta = 97.50(3)degrees, V = 5545.2(2) Angstrom(3), Z = 4, M-r = 1140.80, D-c = 1.366 g/cm(3), F(000) = 2384 and mu(MoKalpha) = 0.289 mm(-1).

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A copper-strontium heterometallic coordination polymer was synthesized and characterized by elemental analysis and IR spectra. The crystal structure was determined by single-crystal X-ray diffraction analyses. The title complex is a 2 D coordination polymer with the chemical formula [[(CuL)(2)Sr (H2O) center dot Sr-2 ((HO)-O-2)(7)]center dot 2H(2)O center dot 0.5CH(3)OH](n), where H4L = N-(2-hydroxybenzamido)-N'-(3-carboxylsalicylidene) ethylenediamine. Its structural unit is comprised of two adjacent units, which polymerized with each other to form a new layered heterometallic coordination polymer.