Crystal Structure of Ethyl 4-benzoyl-1a,2,3,4-tetrahydro-3-methyl-1a-(4-methylphenyl)-1H-azirino〔1,2-a〕〔1,5〕 benzodiazepine-1-carboxylate(C_(28)H_(28)N_2O_3)

１ＩＮＴＲＯＤＵＣＴＩＯＮＢｅｎｚｏｄｉａｚｅｐｉｎｅｃｏｍｐｏｕｎｄｓａｒｅｉｍｐｏｒｔａｎｔｐｈａｒｍａｃｅｕｔｉｃａｌａｇｅｎｔｓ〔１,２〕．Ｒｅｃｅｎｔｌｙｉｔｈａｓｂｅｅｎｆｏｕｎｄｔｈａｔｂｅｎｚｏｄｉａｚｅｐｉｎｅｔｒｉｃｙｃｌｉｃｄｅ...     

局域共振型声学超材料薄板带隙特性的能量解法

研究局域共振型声学超材料的带隙特性时,面临的首要问题是寻求一种带隙特性的高效解法。为此,本文以局域共振型声学超材料薄板为研究对象,提出了一种基于能量泛函变分原理及正交多项式级数展开的带隙计算方法。该方法通过合并基体板及共振子的动、势能及外力功建立元胞的能量泛函,经过变分运算得到元胞的振动控制方程,进而引入第一类Chebyshev正交多项式作为基函数将控制方程进行离散。为克服无法直接对离散控制方程中的广义坐标施加周期边界条件的困难,该方法将连续边界条件弱化到若干选定的配点上以离散方式实现,并将对应的一组线性约束条件通过拉格朗日乘子法施加到系统中。仿真结果表明,该方法具有较高的计算精度和效率,并可应用于\     

几种应变检测的光力学测试方法及其比较

应变测量技术在工程应用中有重要意义.一是它可以直接用来获得应力场,可以用来评价材料的安全性和可靠性;二是应变梯度很大的部位往往又是材料破坏的起始点,所以应变测量又可以用于进行材料的无损检测.当前几种光力学方法受到了重视,即云纹干涉法、电子剪切散斑干涉法和数字相关散斑法,对上述方法的原理、光路设计、特点作了介绍,以便这些传统方法的进一步推广,文中还特别介绍了一种作者近来在国内率先开展的微压痕应变花法.这一方法可以方便用于金属等材料上,可以较精确定量研究测试物体的应变而且对刚体位移不敏感,应用起来更加直接和方便,更有推广和应用前景.本文有利于针对研究对象的特点,选用更加合适的应变测量方法.     

乙二胺溶剂热还原法制备碳纳米管

以乙二胺作为溶剂和碳源,用KBH4还原NiCl2得到的镍作为催化剂,于300℃制备碳纳米管。X-射线衍射(XRD)、透射电子显微镜(TEM)、选区电子衍射(SAED)和Raman光谱分析证明,产品为多壁碳纳米管,直径约为100nm,长度达几微米。该方法具有反应温度低、反应时间短、操作简便等特点。     

(R)-乙基-2-吡啶亚砜与(4R,5R)-TADDOL包结晶体 [C7H9NOS·C31H30O4]的晶体结构分析

（Ｒ）－乙基－２－吡啶亚砜与（４Ｒ，５Ｒ）－二（羟基－二苯基－甲基）－２，２－二甲基－１，３－二氧戊环（ＴＡＤ－ＤＯＬ）可以形成物质的量比为１∶１的手性包结晶体，Ｘ射线衍射分析确定该晶体属单钭晶系，Ｐ２１空间群，ａ＝０．９７０１（２）ｎｍ，ｂ＝０．９９５３（２）ｎｍ，ｃ＝１．７３９２（２）ｎｍ；β＝９２．０７９°（１４），Ｖ＝１．６７８１（５）ｎｍ３，Ｚ＝２，Ｄｃ＝１．２３０ｇ／ｃｍ３，分子式Ｃ３８Ｈ３９ＮＯ５Ｓ，Ｍｒ＝６２１．７６，最终偏离因子Ｒ＝０．０３５１，ＲＷ２＝０．０７７２，Ｆｌａｃｋ值为０．１（２）．结构分析表明，主客体存在分子间氢键．光学纯的ＴＡＤＤＯＬ与消旋的乙基吡啶亚砜（１）作用时，ＴＡＤＤＯＬ对１具有很好的手性识别能力，选择性地与１的一个对映体形成氢键，长成晶体．参照晶体结构确定了１的两个对映体的绝对构型     

Synthesis of 3-Aryl-5-C-Glycosylisoxazoles from Several Aldehydo-Sugar Derivatives

ABSTRACT

The synthesis of several 3-aryl-5-glycosylisoxazole derivatives has been achieved. By condensation of the protected aldehydo-sugars 2,3-O-isopropylidene-D-glyceraldehyde (1), 2,3:4,5-di-O-isopropylidene-aldehydo-D-arabinose (2) and D-xylose (3), and 2,5-anhydro-3,4,5-tri-O-benzoyl-D-mannose (4) with benzoylmethylenetriphenylphosphorane, enulose derivatives were formed, which were later converted into a,ß-unsaturated ketoximes. These ketoximes were oxidatively cyclized with iodine and, after removal of the hydroxyl protecting groups, 3-phenyl-5-glycosylisoxazoles were formed.     

非水溶液滴定法测定普卢利沙星的含量

以0.1mol.L-1高氯酸为滴定液,结晶紫为指示剂,用非水滴定法测定普卢利沙星。重复测定普卢利沙星含量平均值为99.4%(n=6),相对标准偏差为0.1%。该方法准确简便、重复性好,可作为普卢利沙星含量测定的有效方法。     

Reaction of 2,3-O-Isopropylidene-D-Glyceraldehyde and Some Dialkyl and Diarylthiomethyl Sulfoxides: Stereochemical Aspects

Abstract

The reaction of 2,3-O-isopropylidene-D-glyceraldehyde with different dialkyl and diarylthiomethyl sulfoxides occurs with a high selectivity and produces the corresponding 1-alkyl(or l-aryl)-sulfynil-l-alkyl(or 1-aryl) thio-3,4-O-isopropylidene-D-tetroses as pure diastereoisomers. We have determined the absolute configuration of the three chiral centers formed in these reactions.     

Speciation of Cr(VI)/Cr(III) by electrothermal atomisation AAS after electrodeposition on a L'vov platform

Summary The pyrolysed graphite L'vov platform of a tube furnace is considered as an electrode for the electrodeposition and speciation of chromium by electrothermal atomisation atomic absorption spectrometry (ETA-AAS). Firstly, a preliminary study of the Cr(VI)/Cr(III) voltammetric behavior at pH 4.70 on a glassy-carbon electrode is carried out. Secondly, the L'vov platform is used as a cathodic macro-electrode for the selective preconcentration of Cr(VI)/Cr(III) on a mercury film. Speciation of Cr(VI)/Cr(III) is carried out on the basis of the electrolysis potential (E_e): at pH 4.70 and E_e=–0.30 V, only Cr(VI) is reduced to Cr(III) and accumulated as Cr(OH)₃ by adsorption on a mercury film; at E_e=–1.80 V both Cr(VI) and Cr(III) are accumulated forming an amalgam with added mercury(II) ions. Once the film has been formed, the platform is transferred to a graphite tube to atomise the element. The reliability of the method was tested for the speciation of chromium in natural waters and it proves to be highly sensitive thanks to the electroanalytical step. In all samples, the Cr(VI) concentration was less than the detection limit (0.15 ng ml^–1), and the concentration of Cr(III) agrees with those of total chromium. The analytical recovery of Cr(VI) added to water samples [3.50 ng ml^–1 of Cr(VI)] was 105±6.2%.