淋巴细胞膜上Na+/Ca2+交换操纵的Eu3+内流的荧光法研究

利用Fura-2荧光浓度指示剂法、通过检测360nm激发荧光强度的变化,研究了Eu³⁺能否利用人外周血淋巴细胞膜上的Na⁺/Ca²⁺交换进入细胞。结果表明:用ouabain预处理细胞无Na⁺介质中测试,当加入Eu³⁺时,360nm荧光强度发生猝灭,且随着胞外加入的Eu³⁺浓度的增大而猝灭增强。表明在实验条件下Eu³⁺可以进入细胞。电压依赖性Ca     

一步热解法制备Cu/Fe双金属生物炭复合材料及其高效吸附Pb2+性能

使用一步热解法制备了 Cu/Fe双金属生物炭复合材料(BC@Cu/Fe-X,X=3、5、10)和 Fe生物炭复合材料(BC@Fe)。考察了Cu掺杂量对BC@Cu/Fe-X吸附Pb²⁺的影响,确定最佳掺杂比例。结果显示BC@Cu/Fe-5吸附Pb²⁺性能最好。考察了吸附时间、Pb²⁺浓度、pH、背景离子、空气中老化等实验条件对 BC@Cu/Fe-5 吸附 Pb²⁺的影响。通过动力学、热力学数据拟合分析了BC@Cu/Fe-5吸附Pb²⁺的行为,利用X射线粉末衍射(XRD)、X射线光电子能谱(XPS)、傅里叶变换红外光谱(FTIR)等表征手段解析了BC@Cu/Fe-5吸附Pb²⁺前后特征峰变化。BC@Cu/Fe-5吸附Pb²⁺的机理如下：大约42%的Pb²⁺被还原为Pb⁰,33%的Pb²⁺形成PbO/Pb(OH)₂,25%的Pb²⁺与O—H、C—O、C=O、COO、Fe—O等官能团形成配合物。Cu掺杂可以提高Fe还原Pb²⁺的能力。     

改性硅藻土负载亚铁氰化铜复合物的制备及其对Cs+的吸附性能

采用水热法、以氯化铝为铝源对硅藻土(De)进行改性,通过浸渍法将亚铁氰化铜(KCuHCF)纳米颗粒负载于改性De表面,制备出γ-AlOOH/De-KCuHCF和γ-Al₂O₃/De-KCuHCF两种复合吸附剂,对所制备的吸附剂进行了表征,并研究了其对Cs⁺的吸附性能。结果表明,所制备吸附剂具有优异的Cs⁺吸附性能,γ-AlOOH/De-KCuHCF和γ-Al₂O₃/De-KCuHCF最高吸附容量分别可达75.44、84.02 mg·g^-1,γ-Al₂O₃/De-KCuHCF对模拟卤水中Cs⁺的吸附率高达97.55%;以3 mol·L^-1 NH₄NO₃为脱附剂,经3级连续脱附后,γ-Al₂O₃/De-KCuHCF的Cs⁺脱附率可达81.88%,经过5次吸附-脱附循环后仍保持了较高的吸附量。     

用离散-连续模型计算NH2-,NH3和NH4+的溶剂化自由能

通过理论计算推测NH2-,NH3和NH4+在水溶液第一溶剂化层中与之直接作用的水分子分别为2,4和4个,并采用离散-连续模型计算了NH2-,NH3,NH3和NH4+在水溶液中的溶剂化自由能.结果表明,由于离散-连续模型在从头算水平考虑了溶质分子与第一溶剂化层溶剂分子之间的作用,能更准确地描述溶剂化作用.此外,采用更加符合溶液中真实情况的溶剂化构型,能得到更准确的溶剂化性质.     

KMgF3∶Ce3+,Tb3+纳米粒子中Ce3+→Tb3+的发光及能量传递

利用微乳液方法,合成了铈、铽共掺杂的氟镁钾纳米粒子,研究了体系中Ce³⁺→Tb³⁺的发光特性以及它们之间的相互作用,结果表明KMgF₃∶Ce³⁺,Tb³⁺纳米粒子中存在Ce³⁺→Tb³⁺的能量传递过程,即Ce³⁺可以将吸收的能量直接传递给Tb³⁺离子,使得Tb³⁺的绿色发光强度大为增加。     

CaWO4:xEu3+,ySm3+,zLi+红色荧光粉的制备及光学性能

采用微波固相法制备了CaWO₄：xEu³⁺,ySm³⁺,zLi⁺红色荧光粉。测量样品的XRD图、激发谱、发射谱及发光衰减曲线,研究并分析了Eu³⁺、Sm³⁺、Li⁺的掺杂浓度,对样品微结构、光致发光特性、能量传递及能级寿命的影响。结果表明,Eu³⁺、Sm³⁺、Li⁺掺杂并未引起合成粉体改变晶相,仍为CaWO₄单一四方晶系结构。Eu³⁺、Sm³⁺共掺样品中,Sm³⁺掺杂为3%时,Sm³⁺对Eu³⁺的能量传递最有效。Li⁺掺杂起到了助熔剂和敏化剂的作用,使样品发光更强。在394 nm激发下,与CaWO₄：3%Eu³⁺样品比较,3%Eu³⁺、3%Sm³⁺共掺CaWO₄及3%Eu³⁺、3%Sm³⁺、1%Li⁺共掺CaWO₄样品的发光分别增强2倍及2.4倍。同一激发波长下,单掺Eu³⁺样品寿命最短,Sm³⁺、Eu³⁺共掺样品随Sm³⁺浓度增加,寿命先减小后增加,且掺杂了Li⁺的样品比不掺Li⁺的样品⁵D₀能级寿命有所增加。     

Eu2+、Mn2+、Sr2+掺杂BaMgAl10O17的燃烧法合成及光致发光性能研究

在600℃温度下,采用液相燃烧法合成了Sr²⁺、Eu²⁺和Mn²⁺三掺的BaMgAl₁₀O₁₇（BAM）蓝绿荧光粉。用XRD、SEM和荧光光谱仪分别分析和表征该荧光粉的物相、形貌和光致发光性能。结果表明,液相燃烧法合成BAM的温度明显低于传统的高温固相合成法;合成的纳米棒均匀、无团聚现象;荧光光谱仪分析表明Eu²⁺、Mn²⁺离子间存在能量传递,且Sr²⁺能有效提高BAM的发光强度,约为固相法制备荧光强度的1.8倍。BAM：0.1Eu²⁺,0.04Mn²⁺,0.05Sr²⁺色坐标为（0.146,0.250）,属于蓝绿光。     

蓝色长余辉材料CaAl2O4:Eu2+,Nd3+的合成及其发光性能

采用高温固相法合成了系列单相Ca(1-x-y)Al2O4:Eu2+x,Nd3+y(0≤x≤0.045,0≤y≤0.0037)粉末样品,并表征了其发光特性.研究结果表明,样品的发射光谱为最大发射峰位于440nm的宽带谱,属于Eu2+的4f65d→4f7跃迁.通过对Eu2+,Nd3+掺杂量与样品发光性能之间关系的研究发现,Eu2+和Nd3+最佳掺杂量分别为x=0.00125和y=0.0025,并且Nd3+对改善蓝色长余辉材料CaAl4:Eu2+的余辉性能具有重要的作用.在最佳掺杂条件下,样品的余辉时间可达1000min,初始亮度大于1200mcd/m2,60min后发光粉的亮度仍然在10mcd/m2以上.利用正电子湮灭技术和热释光技术,研究了Eu2+和Nd3+对CaAl2O4:Eu2+,Nd3+材料的发光性能的影响.     

Fura-2探针对希土Y3+跨PC12细胞膜行为研究

使用AR-MIC-CM阳离子测定系统,发展Fura-2荧光测定技术,将其应用于测定细胞内游离希土离子Y³⁺,并以此研究了Y³⁺跨PC12细胞(大鼠嗜铬细胞瘤细胞)膜的行为。结果表明：在模拟细胞内各离子组分,pH=7.05的溶液中,测得表观解离常数为4.5p mol·L^-1。对于PC12细胞,静息条件下Y³⁺不能跨越细胞膜进入胞内。与钙离子通道相关的KCl和去甲肾上腺素均不能刺激希土Y³⁺过膜。用Ouabain(哇巴因)使胞内Na⁺超载后,Y³⁺可过膜进入细胞内,且过膜量与胞外Y³⁺浓度和胞内Na⁺超载程度有一定的浓度依赖关系,提示Y³⁺可以经由Na⁺/Y³⁺交换机制过膜而进入细胞内。     

CaSb2O6:Bi3+,Eu3+荧光粉的制备和发光性质

采用共沉淀法及1 200 ℃后续煅烧4 h,成功制备了CaSb₂O₆:Bi³⁺,Eu³⁺荧光粉,并对其结构及发光性能进行了研究。所制备荧光粉颗粒为六边形类圆饼状,平均尺寸在100~600 nm之间。对CaSb₂O₆:Bi³⁺,Eu³⁺发光的机理分析表明,Bi³⁺对Eu³⁺的发光存在高效的敏化与能量传递。当Bi³⁺和Eu³⁺的掺杂浓度分别为0.5%和8%,Eu³⁺位于580 nm(⁵D₀→⁷F₀ )处的荧光发射显著增强,Bi³⁺,Eu³⁺共掺样品的荧光强度是CaSb₂O₆:Eu³⁺的10倍左右。调节Bi³⁺/Eu³⁺离子掺杂比,色坐标呈现了从蓝、白光到红光的变化,表明该荧光粉可分别作为蓝或红色荧光粉使用,甚至可实现从蓝、白光到红光的自由调控,这为白光LED荧光粉的发展提供了参考。     

乳酸杆菌A09吸附还原Ag（Ⅰ）的谱学表征

Pooley[1]发现氧化亚铁硫杆菌(Thiobacillusferroxidans)和氧化硫硫杆菌(Thiobacillusthiooxidans)能在其细胞表面累积银,形成Ag2S,每克干重细胞吸附250mgAg2S.文献[2]也报导了类似的研究结果.一些霉菌也具有吸收金、银等重金属的能力[3].Brierley等[4]研究了用微生物制备回收贵金属的去除剂(MRA),用它能从摄影废液中回收银,每克MRA累积94mgAg;同时指出,贵金属生物吸附也包含金属离子被还原为金属的过程.在微生物吸附还原贵金属前期研究[5－9]的基础上,我们从金、银矿土等不同来源的细菌菌株中,筛选获得一株吸附、还原Ag＋…     

Biosorption of lead(II) from aqueous solutions by non-living algal biomass Oedogonium sp. and Nostoc sp.--a comparative study

Industrial wastewaters containing heavy metals pose a major environmental problem that needs to be remedied. The present study reports the ability of two non-living (dried) fresh water algae, Oedogonium sp. and Nostoc sp. to remove lead(II) from aqueous solutions in batch system under varying range of pH (2.99-7.04), contact time (5-300 min), biosorbent dose (0.1-0.8 g/L), and initial metal ion concentrations (100 and 200mg/L). The optimum conditions for lead biosorption are almost same for the two algal biomass Oedogonium sp. and Nostoc sp. (pH 5.0, contact time 90 and 70 min, biosorbent dose 0.5 g/L and initial Pb(II) concentration 200mg/L) however, the biomass of Oedogonium sp. was found to be more suitable than Nostoc sp. for the development of an efficient biosorbent for the removal of lead(II) from aqueous solutions, as it showed higher values of q(e) adsorption capacity (145.0mg/g for Oedogonium sp. and 93.5mg/g for Nostoc sp.). The equilibrium data fitted well in the Langmuir isotherms than the Freundlich isotherm, thus proving monolayer adsorption of lead on both the algal biomass. Analysis of data shows that the process involves second-order kinetics and thermodynamic treatment of equilibrium data shows endothermic nature of the adsorption process. The spectrum of FTIR confirms that the amino and carboxyl groups on the surface of algal biomass were the main adsorption sites for lead removal. Both the biosorbents could be regenerated using 0.1 mol/L HCl solution, with upto 90% recovery. The biosorbents were reused in five biosorption-desorption cycles without a significant loss in biosorption capacity. Thus, this study demonstrated that both the algal biomass could be used as an efficient biosorbents for the treatment of lead(II) bearing wastewater streams.     

Accumulation of Silver(I) Ion and Diamine Silver Complex by <Emphasis Type="Italic">Aeromonas</Emphasis> SH10 biomass

The biomass of Aeromonas SH10 was proven to strongly absorb Ag⁺ and [Ag(NH₃)₂]⁺. The maximum uptake of [Ag(NH₃)₂]⁺ was 0.23 g(Ag) g⁻¹(cell dry weight), higher than that of Ag⁺. Fourier transform infrared spectroscopy spectra analysis indicated that some organic groups, such as amide and ionized carboxyl in the cell wall, played an important role in the process of biosorption. After SH10 cells were suspended in the aqueous solution of [Ag(NH₃)₂]⁺ under 60°C for more than 12 h, [Ag(NH₃)₂]⁺ was reduced to Ag(0), which was demonstrated by the characteristic absorbance peak of elemental silver nanoparticle in UV-VIS spectrum. Scanning electron microscopy and transmission electron microscopy observation showed that nanoparticles were formed on the cell wall after reduction. These particles were then confirmed to be elemental silver crystal by energy dispersive X-ray spectroscopy, X-ray diffraction, and UV-VIS analysis. This study demonstrated the potential use of Aeromonas SH10 in silver-containing wastewater treatment due to its high silver biosorption ability, and the potential application of bioreduction of [Ag(NH₃)₂]⁺ in nanoparticle preparation technology.     

巨大芽孢杆菌D01吸附金(AU3+)的谱学表征

对休眠的巨大芽孢杆菌(Bacillus megatherium)D01菌体吸附Au^3 的作用过程进行了谱学表征．运用AAS考察了pH、时间和温度对D01菌体吸附Au^3 过程的化学动力学和热力学相关参数的影响．D01菌粉中硫元素含量的EDX分析说明该菌体中对Au^3 具有还原作用的L-半胱氨酸和蛋氨酸的含量极少;D01菌体水解后葡萄糖含量的UV-vis测定说明该菌体水解产物中含有一定量的还原糖,空白的和吸附Au^3 的D01菌体的FFIR检测表明该菌体细胞壁肽聚糖层糖类化合物的羟基和肽链侧链氨基酸残基离子化羧基为吸附Au^3 的活性基团;肽聚糖层部分多糖的水解产物低聚糖、二糖及单糖等还原糖的半缩醛羟基游离态醛基为电子供体,将Au^3 原位还原成Au^0．葡萄糖和Au^3 相互作用的XRD和FFIR表征证明Au^3 是在还原糖的醛基上直接被还原成Au^0．     

Characteristic of the Ag(bipy) 2 2+ /Ag(bipy) 2 + and Ag(phen) 2 2+ /Ag(phen) 2 + systems in acetonitrile

The values of standard potentials of redox systems formed by the complexes of Ag(II) and Ag(I) with 2,2-bipyridine and 1,10-phenanthroline in acetonitrile have been determined. The properties of the above systems in water and acetonitrile are compared. The possibility of application of these systems for the construction of electrodes with a constant potential in different solvents is discussed.

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Charakteristik der Systeme Ag(bipy) ₂ ²⁺ /Ag(bipy) ₂ ⁺ und Ag(phen) ₂ ²⁺ /Ag(phen) ₂ ⁺ in Acetonitril

Zusammenfassung Die Standardpotentialwerte der Redoxsysteme, die durch Komplexbildung von Ag(II)- und Ag(I)-Ionen mit 2,2-Bipyridin und 1,10-Phenantrolin gebildet werden, wurden in Acetonitril bestimmt. Die Eigenschaften dieser Redoxsysteme in Wasser und Acetonitril wurden verglichen.Es wurde weiterhin die Möglichkeit der Anwendung dieser Systeme zur Konstruktion einer Elektrode mit unveränderbarem Potential in verschiedenen Lösungsmitteln diskutiert.

     

醇和N,N-二甲基乙酰胺分子间相互作用的FTIR光谱研究

The association between alcohols and N,N-dimethylacetamide in carbon tetrachloride was investigated using FTIR spectroscopy at 298 K.The formation constants for 1∶1 and 1∶2 complexes were calculated using the method of Whetsel and Kagarise.The observed 1∶1 complex values were also verified using the method of Nash.The rate of change in C=O bond moment on complexing with alcohols increased with increasing acidity of alcohols.The formation constant and values of free energy change increased with the increase in carbon chain length of alcohols,which suggested that the degree of complex formation varied with the length of the carbon chain of alcohols.     

正常与癌症肺组织的傅里叶变换红外光谱差异的研究

傅里叶变换红外(FTIR)光谱可以在分子水平上研究细胞和组织等复杂的生命体系,提供分子结构和组成的信息.我们发展了一种用于直接测定肿瘤及正常组织红外光谱的方法,对16例肺癌及其癌旁正常组织进行了测定.结果表明,对于正常和癌变的肺组织,FTIR光谱中存在显著差异,相关谱带的相对峰高比可以表征这些差异.因此,傅里叶变换红外光谱可以用来诊断癌症与正常的肺组织,有望成为肿瘤快速诊断的新方法.     

The Ag+-G interaction inhibits the electrocatalytic oxidation of guanine--a novel mechanism for Ag+ detection

The heavy metal ions-nucleobases interaction is an important research topic in environmental and biochemical analysis. The presence of the silver ion (Ag⁺) may influence the formation of oxidation intermediate and the electrocatalytic oxidation activity of guanine (G), since Ag⁺ can interact with guanine at the binding sites which are involved in the electrocatalytic oxidation reaction of guanine. According to this principle, a new electrochemical sensor for indirectly detecting Ag⁺ based on the interaction of Ag⁺ with isolated guanine base using differential pulse voltammetry (DPV) was constructed. Among the heavy metal ions examined, only Ag⁺ showed the strongest inhibitory effect on the electrocatalytic oxidation of guanine at the multi-walled carbon nanotubes modified glassy carbon electrode (CNTs/GC). And the quantitative study of Ag⁺ based on Ag⁺-G sensing system gave a linear range from 100 nM to 2.5 μM with a detection limit of 30 nM. In addition, this modified electrode had very good reproducibility and stability. The developed electrochemical method is an ideal tool for Ag⁺ detection with some merits including remarkable simplicity, low-cost, and no requirement for probe preparation.