一氧化氮对海洋浮游植物生长影响的规律及其化学特征研究

选用了青岛大扁藻、亚心型扁藻、中肋骨条藻和小新月菱形藻四种海藻, 进行一氧化氮(NO)对其生长影响的实验, 初步从化学角度研究了一氧化氮对海洋浮游植物生长的具体影响规律. 结果发现: (1) 一次性加入不同浓度NO或每天两次加入不同浓度NO, 这四种藻的生长在f/2或f/50培养液中均显示出明显的促进或抑制作用; (2) NO对海洋浮游植物生长的影响均呈峰形, 不同浮游植物有不同的最佳NO峰值, 这与NO对高等植物生长的作用效果是基本一致的; (3) 一氧化氮对实验中所用的青岛大扁藻(非赤潮藻)与中肋骨条藻和小新月菱形藻(赤潮藻)的影响情况是不同的; (4) 提出“NO阈”的观点. 这些都可能为赤潮发生机理的研究提供新的思路.     

Electrochemical Determination of Methyltin Compounds

 The electrochemical behaviour of monomethyltin, dimethyltin and trimethyltin compounds in 20% (V/V) methanol/water solution, 0.05 mol/L in tetraethylammonium perchlorate at pH 2.5, has been investigated by differential pulse polarography and differential pulse anodic stripping voltammetry. In differential pulse polarography, dimethyltin and trimethyltin gave one reversible wave with peak potentials at −0.70 V and −1.07 V, respectively. Detection limits were 6.6 × 10⁻⁷ mol/L for dimethyltin and 4.1 ×  10⁻⁶ mol/L for trimethyltin. The electrochemistry of monomethyltin was found to be more complex. By differential pulse anodic stripping voltammetry, monomethyltin, dimethyltin and trimethyltin produced distinct stripping peaks (−0.39 V, −0.75 V and −1.14 V, respectively), which allow to determine these compounds at trace levels. Using this new method, detection limits were: 1.2 × 10⁻⁷ mol/L for monomethyltin, 1.7 × 10⁻⁷ mol/L for dimethyltin and 1.4 × 10⁻⁶ mol/ L for trimethyltin. For monomethyltin, a second peak (E_p = −0.60 V), less sensitive (detection limit of 2.5 × 10⁻⁶ mol/L), was also observed at concentrations above 4.2 × 10⁻⁷ mol/L. Recoveries of methyltin compounds added separately to tap water samples at the 0.42–16.9 μmol per litre level ranged from 84.5 to 99.8% depending upon the methyltin species. Received January 3, 2001. Revision August 10, 2001.     

Sr含量对La2-xSrxNiO4 (x = 0.0~1.2)上NO分解的影响

研究了Sr含量对La_2&;#8722;xSr_xNiO₄上氧化还原性能和NO分解的影响, 发现活性在x = 0.6时达到最大值. TPD和TPR等的表征结果说明样品在x = 0.6时具有比较匹配的氧化、还原能力, 从而使O₂的脱附和NO的吸附变的相对容易, 提高了催化活性. 研究结果说明在T<700℃时, O₂的脱附比较困难, 是NO分解反应的速控步骤; 随着反应温度的增加(T>700℃), O₂的脱附变的容易, NO的活化吸附(NO + V_o + Ni²⁺→NO^&;#8722;-Ni³⁺)成为反应的速控步骤. 氧空位的存在是NO分解的前提条件, 但氧空位的量与反应活性并不是呈正比关系.     

Diffusion of Noble Metals,Zn and Ge in GaSb Single Crystals

Diffusion of Cu, Ag, Au, Ge and Zn in single crystal gallium antimonide has been carried out by measuring Hall effect according to van der Pauw, conductivity, energy dispersive X-ray (EDX) and surface electron microscopy. The best results have been obtained in excess of antimony. The resulting diffusion data in GaSb are diffusivity D_o, activation enthalpy Q, carrier density p and mobility μ at 300 K: Ag: D_o=1.8·10⁻⁴ cm² s⁻¹, Q=1.2 eV, p=6·10¹⁸ cm⁻³, μ=550 cm² (Vs)⁻¹ Au: D_o=6.6·10⁺³ cm² s⁻¹, Q=2.7 eV, p=5·10¹⁸ cm⁻³, μ=500 cm² (Vs)⁻¹ Cu: D_o=3.2·10⁺⁸ cm² s⁻¹, Q=2.7 eV, p=2·10¹⁸ cm⁻³, μ=150 cm² (Vs)⁻¹ Zn: D_o=9.2·10⁻² cm² s⁻¹, Q=1.8 eV, p=2·10²⁰ cm⁻³, μ=80 cm² (Vs)⁻¹ Ge: D_o=1.0·10⁻¹ cm² s⁻¹, Q=1.7 eV, p=1·10¹⁹ cm⁻³, μ=320 cm² (Vs)⁻¹. This revised version was published online in August 2006 with corrections to the Cover Date.     

Determination of Nickel in Fuel Ethanol Using a Carbon Paste Modified Electrode Containing Dimethylglyoxime

A mercury-free electrode chemically modified with carbon paste containing dimethylglyoxime was used for determination of nickel in fuel ethanol. The instrumental parameters and composition of the modified paste were optimized. The analytical curve for nickel determination from 5.0 × 10⁻⁹ to 5.0 × 10⁻⁷ mol L⁻¹ was obtained using 25 min of accumulation time. The detection limit and amperometric sensitivity obtained for this method were 2.7 × 10⁻⁹ mol L⁻¹ and 5.2 × 10⁸ μA mol⁻¹ L, respectively. The values for nickel concentration in four commercial samples of fuel ethanol were obtained in the range of 1.1 × 10⁻⁸ to 6.9 × 10⁻⁸ mol L⁻¹. A comparison to graphite furnace atomic absorption spectrometry (GFAAS) was performed for nickel determination in commercial samples of ethanol.     

Kinetics and the Mechanism of Iron(II) Reduction of cis-α-halogeno(cetylamine) (triethylenetetramine)cobalt(III) Complex Ion in Aqueous Acid Medium

The kinetics and mechanism of iron(II) reduction of cis- α-chloro/bromo(cetylamine)(triethylenetetramine) cobalt(III) surfactant complex ions were studied spectrophotometrically in an aqueous acid medium by following the disappearance of Co^III using an excess of the reductant under pseudo-first-order conditions: [Fe^II = 0.25 mol dm⁻³, [H⁺ = 0.1 mol dm⁻³, [μ = 1.0 mol dm⁻³ ionic strength in a nitrogen atmosphere at 303, 308 and 313 K. The reaction was found to be second order and showed acid independence in the range [H⁺ = 0.05−0.25 mol dm⁻³. The second order rate constant increased with Co^III concentration and the presence of aggregation of the complex itself altered the reaction rate. The effects of [Fe^II], [H⁺] and [ μ] on the rate were determined. Activation and thermodynamic parameters were computed. It is suggested that the reaction of Fe²⁺(aq) with Co^III complex proceeds by an inner-sphere mechanism.     

Microdialysis sampling and chemiluminescence detection for in vivo and real-time study of the lead metabolism in rabbit blood

The chemiluminescence (CL) system K₂MnO₄-luminol is shown to be useful for the determination of lead(II). The method is based on the catalytic effect of Pb(II) on the CL reaction. The linear range was 3 × 10⁻³–9 × 10⁻¹ mg L⁻¹ (r = 0.9971) and the relative standard deviation (R.S.D.) for 5 × 10⁻² mg L⁻¹ Pb(II) measurement was 0.7% (n = 11). The detection limit was 3 × 10⁻⁴ mg L⁻¹ (3σ) Pb(II). Based on this, an in vivo, on-line, real-time analytical system for monitoring the metabolism of free lead(II) in rabbit blood was developed. A microdialysis probe, implanted in the vein of a rabbit, was perfused with perfusate at a flow rate of 5 μL min⁻¹. The concentration of free lead(II) in the dialysate was determined on-line with a flow-injection CL system. This system included microdialysis sampling, on-line separation and chemiluminescence detection. The concentration-time curve of lead(II) was in accordance with the one-compartmental open model, T_1/2 (elimination half-life), T_max (peak time) and C_max (peak concentration) were 37.77 min, 85.20 min and 0.137 mg L⁻¹, respectively.     

Electrocatalytic oxidation of dopamine at an ionic liquid modified carbon paste electrode and its analytical application

A room-temperature ionic liquid N-butylpyridinium hexafluorophosphate was used as a binder to construct an ionic liquid modified carbon paste electrode, which was characterized by scanning electron microscopy and electrochemical impedance spectroscopy. The ionic liquid carbon paste electrode (IL-CPE) showed enhanced electrochemical response and strong analytical activity towards the electrochemical oxidation of dopamine (DA). A pair of well-defined quasireversible redox peaks of DA appeared, with the redox peaks located at 215 mV (E _pa) and 151 mV (E _pc) (vs. the saturated calomel electrode, SCE) in pH 6.0 phosphate buffer solution. The formal potential (E ^0′) was calculated as 183 mV (vs. SCE) and the peak-to-peak separation as 64 mV. The electrochemical behavior of DA on the IL-CPE was carefully investigated. Under the optimal conditions, the anodic peak currents increased linearly with the concentration of DA in the range 1.0 × 10⁻⁶–8.0 × 10⁻⁴ mol/L and the detection limit was calculated as 7.0 × 10⁻⁷ mol/L (3σ). The interferences of foreign substances were investigated and the proposed method was successfully applied to the determination of DA injection samples. The IL-CPE fabricated was sensitive, selective and showed good ability to distinguish the coexisting ascorbic acid and uric acid.     

Synthesis and characterization of poly(styrene/α-t-butoxy-ω-vinylbenzyl-polyglycidol) microspheres

Polystyrene microspheres with polyglycidol (polyGL) in a surface layer were synthesized in batch radical emulsifier-free emulsion copolymerizations of styrene and surfmers, α-t-butoxy-ω-vinylbenzyl-polyGL macromonomers (VB-polyGL). Macromonomers with number-average molecular weight Mˉ _n=950 (VB-polyGL950) and Mˉ _n=2700 (VB-polyGL2700) were used for these polymerizations. In all syntheses the initial concentrations of styrene and initiator (K₂S₂O₈) were constant. The initial macromonomer-to-styrene ratios were varied from 1.10 × 10⁻³ to 1.64 × 10⁻² mol/mol and from 3.46 × 10⁻⁴ to 3.47 × 10⁻³ mol/mol for VB-polyGL950 and VB-polyGL2700, respectively. The diameters of microspheres obtained were smaller for the syntheses with higher concentrations of macromonomers. Syntheses with VB-polyGL950 yielded microspheres with number-average diameters (Dˉ _n) from 216 to 900 nm and with a bimodal diameter distribution. The number-average diameters of microspheres obtained with VB-polyGL2700 varied from 220 to 650 nm, depending on the initial concentration of macromonomer. Their diameter distributions were monomodal, with a diameter polydispersity parameter (ratio of weight-average and number-average diameters) in the range 1.007≤Dˉ _w/Dˉ _n≤1.022. For each type of microsphere the fraction of polyGL in a surface layer and the surface concentration of sulfate anions were determined. The fraction of polyGL in the surface layer was related to the initial monomer composition in the polymerizing mixture. Adsorption of human serum albumin onto surfaces of some poly(styrene/VB-polyGL) microspheres was up to 10 times lower than for the polystyrene microspheres obtained in a similar emulsifier-free emulsion polymerization of styrene. Received: 26 September 2000/Accepted: 19 February 2001     

Profile distribution of As(III) and As(V) species in soil and groundwater in Bozanta area

The profile distribution of arsenic(III) and arsenic(V) species in soil and groundwater was investigated in the samples collected in 2005 from a hand-drilled well, in the Bozanta area, Baia Mare region, Romania. The total content of arsenic in the soil was in the range of 525–672 mg kg⁻¹ exceeding 21–27 times the action trigger level for sensitive soil. 0.9–11.3 % of the total content was soluble in water, 83.0–92.6 % in 10 mol dm⁻³ HCl and 2.6–13.3 % was the residual fraction. Arsenic(V) was the dominant arsenic species in the soil in the range of 405–580 mg kg⁻¹. The distribution and mobility of arsenic species was governed by soil pH and contents of Al, Fe, and Mn. The mobility of arsenic(V) decreased with depth, while that of arsenic(III) was high at the surface and in the proximity of groundwater. The total concentration of arsenic in groundwater was (43.40 ± 1.70) μg dm⁻³, which exceeded the maximum contaminant level of 10 μg dm⁻³. Presented at the 33rd International Conference of the Slovak Society of Chemical Engineering, Tatranské Matliare, 22–26 May 2006.     

A simple linear sweep voltammetric method for the determination of double-stranded DNA with malachite green

In pH 3.5 Britton—Robinson buffer solution double-stranded (ds) DNA can react with malachite green (MG) to form an interaction complex, which resulted in the decrease of the electrochemical response of MG, MG had a well-defined second-order derivative linear sweep voltammetric peak at −0.73 V (vs. SCE). After the addition of dsDNA into MG solution, the reductive peak current decreased with the positive shift of peak potential, which was the typical characteristic of intercalation. Based on the interaction, an indirect electrochemical determination method for dsDNA was established. The optimum conditions for the reaction were investigated and there were little or no interferences from the commonly coexisting substances. The decrease of peak current was linear with the concentration of dsDNA over the range of 0.8–12.0 μg cm⁻³ with the linear regression equation as ΔI _p″/nA = 91.70 C/(μg cm⁻³) + 74.55 (n = 10, γ = 0.990). The detection limit was calculated as 0.46 μg cm⁻³ (3σ). The method had high sensitivity and was further applied to the dsDNA synthetic samples with satisfactory result. The interaction mechanism was discussed with the intercalation of DNA-MG to form a supramolecular complex and the stoichiometry of the supramolecular complex was calculated by electrochemical method with the binding number 3 and the binding constant 2.35 × 10¹⁵ (mol dm⁻³)⁻³.     

New Colorimetric Methods for the Determination of Indapamide and its Formulations

 Two simple and sensitive methods for the determination of indapamide in pure and in dosage forms are developed. These methods are based on the oxidation of indapamide with iron(III) in acidic medium. The liberated iron(II) reacts with 1,10-phenanthroline (Method A) and the ferroin complex is colorimetrically measured at λ_max 509 nm against reagent blank. Method B is based on the reduction of Fe(III) by the drug. Iron(II) forms a colored complex (λ_max 522 nm) with 2,2′-bipyridyl. Optimization of the experimental conditions is described. Beer’s law is obeyed in the concentration range 1.0–12 μg ml⁻¹ and 4.0–18 μ g ml⁻¹ for A and B, respectively. The apparent molar absorptivity and Sandell sensitivity for method A is 3 × 10⁴ L mol⁻¹ cm⁻¹ and 0.0188 μ g cm⁻², while for method B is 2.3 × 10⁴ L mol⁻¹ cm⁻¹ and 0.0159 μg cm⁻². The detection and quantification limits are calculated. The developed methods are applied successfully for the determination of indapamide in pure and in tablet form without interference from common excepients. Received November 10, 2000. Revision April 6, 2001.     

Immobilization of Hexacyanoferrate on a Gold Self-Assembled Monolayer, and its Application as a Sensor for Ascorbic Acid

Hexacyanoferrate (II/III) (HCF) was immobilized on a gold electrode modified with cysteamine (CSTE). The Au/CSTE/HCF/PLL electrode was prepared with layer-by-layer (LBL) technique with HCF and poly-d-lysine (PLL). The Au/CSTE/HCF/PLL electrode presented the electrocatalytic activity for ascorbic acid oxidation. The maximum electrocatalytic current was reached at 0.28 V vs SCE in 0.01 mol L⁻¹ TRIS buffer, at pH 7.0. The Au/CSTE/HCF/PLL electrode response was stable under various oxidation–reduction cycles in TRIS medium, showing that the system is very stable. The solution pH has no effect on the anodic peak potential and anodic peak current in the range from 4 up to 10. The intensity of the anodic peak current varied with the concentration of ascorbic acid from 1 up to 910 μmol L⁻¹, with a sensitivity of 62.9 nA cm⁻² L μmol⁻¹, a detection limit of 0.65 μmol L⁻¹ and a quantification limit of 2.2 μmol L⁻¹. The developed sensor was successfully applied for ascorbic acid determination in pharmaceutical samples. The results compared to those obtained with a reference method were statistically the same with 95% of confidence level.     

Kinetics of the Reactions between [(RS)2Fe(µ-S)2M(µ-S)2Fe(SR)2] n− (M = Mo, R = Ph, n = 2; M = V, R = Et, n = 3) and [Fe(SR)4]2−: Key Steps in the Assembly of Cuboidal Fe—S-based Clusters

The reaction of [S₂Mo(μ-S)₂Fe(SPh)₂]²⁻ with [Fe(SPh)₄]²⁻ produces the dicuboidal cluster [{MoFe₃S₄(SPh)₃}₂(μ-(SPh)₃]³⁻ in a three stage process studied by ¹H-n.m.r. spectroscopy and stopped-flow spectrophotometry. The initial stage involves the formation of the linear trinuclear [(PhS)₂Fe(μ-S)₂Mo(μ-S)₂Fe(SPh)₂]²⁻ and the kinetics indicate an equilibrium reaction (k₁^Mo = 2.5±0.3x 10² dm³ mol⁻¹ s⁻¹, k₋₁^Mo = 0.8±0.1 s⁻¹). The second stage involves the reduction of [(PhS)₂Fe(μ-S)₂Mo(μ-S)₂Fe(SPh)₂]²⁻ by [Fe(SPh)₄]²⁻ to form [(PhS)₂Fe(μ-S)₂Mo(μ-S)₂Fe(SPh)₂]³⁻ which subsequently rearranges to form the voided cuboidal [MoFe₂S₄(SPh)₃]²⁻. The kinetics of the second stage exhibits a simple first order dependence on the concentrations of both [(PhS)₂Fe(μ-S)₂Mo(μ-S)₂Fe(SPh)₂]³⁻ and [Fe(SPh)₄]²⁻ (k₂^Mo = 25 ± 2 dm³ mol⁻¹ s⁻¹). The Kinetics of the third stage have not been studied but must involve incorporation of the final Fe and formation of the dicuboidal [{MoFe₃S₄(SPh)₃}₂(μ-SPh)₃]³⁻. The kinetics of the reaction between [(EtS)₂Fe(μ-S)₂V(μ-S)₂Fe(SEt)₂]³⁻ and [Fe(SEt)₄]²⁻ to form [{VFe₃S₄(SEt)₃}₂(μ-SEt)₃]³⁻ have also been studied. An important difference between this reaction and the formation of the analogous [{MoFe₃S₄(SPh)₃}₂(μ-SPh)₃]³⁻ is that the formation of [{MoFe₃S₄(SPh)₃}₂(μ-SPh)₃]³⁻ from [(PhS)₂Fe(μ-S)₂Mo(μ-S)₂Fe(SPh)₂]²⁻ involves a change in the redox state of the cluster, whilst the formation of [{VFe₃S₄(SEt)₃}₂(μ-SEt)₃]³⁻ from [(EtS)₂Fe(μ-S)₂V(μ-S)₂Fe(SEt)₂]³⁻ requires no change in redox state. The reaction between [(EtS)₂Fe(μ-S)₂V(μ-S)₂Fe(SEt)₂]³⁻ and [Fe(SEt)₄]²⁻ involves two stages. The kinetics of the faster phase is associated with a rate law analogous to that observed for the reaction between [(PhS)₂Fe(μ-S)₂Mo(μ-S)₂ Fe(SPh)₂]²⁻ with [Fe(SPh)₄]²⁻: a first order dependence on the concentrations of [(EtS)₂Fe(μ-S)₂V(μ-S)₂Fe(SEt)₂]³⁻ and [Fe(SEt)₄]²⁻ (k₂^V = 1.1±0.1 x 10³ dm³ mol⁻¹ s⁻¹. This observation indicates that whilst there is no change in redox state between [(EtS)₂Fe(μ-S)₂V(μ-S)₂Fe(SEt)₂]³⁻ and [{VFe₃S₄(SEt)₃}₂(μ-SEt)₃]³⁻, reduction is necessary to catalyse the conversion of the linear [(EtS)₂Fe(μ-S)₂V(μ-S)₂Fe(SEt)₂]³⁻ into the voided cuboidal [VFe₂S₄(SEt)₃]³⁻. The results of the studies reported in this paper together with those on other putative reactions involved in the assembly of cuboidal clusters, have been combined to present a scheme of the mechanism of cuboidal cluster assembly. Electronic supplementary material Electronic supplementary material is available for this article at and accessible for authorised users.     

Indirect determination of free cyanide in water and industrial waste water by flow injection-atomic absorption spectrometry

A simple and rapid flow injection system is proposed for indirect determination of cyanide by flame atomic absorption spectrometry. It consists of a microcolumn of immobilized salen (N,N′-bis(salicylidene)ethylenediamine) on sodium dodecyl sulfate (SDS)-coated alumina saturated with silver ion and a carrier of dilute solution of sodium hydroxide (10⁻⁵ mol L⁻¹). The micro-column was located between the injection valve and nebulizer of atomic absorption spectrometry. Injection of 250 μL of aqueous cyanide standard or sample solution at pH range of 9–11 cause elution of silver as silver cyanide complexes, which was then measured by flame atomic absorption spectrometry. The absorbance was proportional to the concentration of cyanide in the sample. The graph of absorbance (as peak height) vs. cyanide concentration was linear over the concentration range of 0.1–10 mg L⁻¹ of cyanide, and the detection limit was 0.06 mg L⁻¹. The relative standard deviation at 1 and 3 mg L⁻¹ of cyanide concentration were 4.1 and 4.7%, respectively. The method was successfully applied to determination of cyanide in water and industrial waste waters, and the accuracy was examined through independent analysis by accepted method of pyridine-barbituric acid.     

Electrochemical determination of malachite green using a multi-wall carbon nanotube modified glassy carbon electrode

A multi-wall carbon nanotube (MWNT) film-modified electrode is described for the determination of malachite green (MG). The electrochemical profile of MG was examined using cyclic voltammetry (CV) and differential pulse voltammetry (DPV), suggesting that the MWNT film facilitates the electron transfer of MG in terms of a potential shift and then significantly enhances the oxidation peak current of MG. The experimental parameters, such as supporting electrolyte, thickness of MWNT film, scan rate and accumulation time, were optimized. Consequently, a sensitive and convenient electrochemical method is proposed for the determination of MG. The oxidation peak current is proportional to the concentration of MG over the range from 5.0 × 10⁻⁸ to 8.0 × 10⁻⁶ mol L⁻¹ obeying the following equation: i_p = 0.09 + 1.19 × 10⁷ C (r = 0.995, i_p in μA, C in mol L⁻¹). The detection limit is 6.0 × 10⁻⁹ mol L⁻¹ (signal to noise = 3) after 5 min of accumulation. Moreover, this method possesses good reproducibility (RSD is 5.6%, n = 8) as well as long-term stability. Finally, the new method was employed to determine MG in fish samples. Correspondence: W. Huang, Department of Chemistry, Hubei Institute for Nationalities, Enshi 445000, P.R. China     

Selective solid-phase extraction of Cu(II) using freshly precipitated lead diethyldithiocarbamate and its spectrophotometric determination

A new solid-phase extraction method has been developed for the selective extraction of Cu(II) in an aqueous system using freshly precipitated lead diethyldithiocarbamate (Pb(DDTC)₂) as a reagent. The method is based on the quantitative replacement of Pb(II) ions in the solid Pb(DDTC)₂ phase by Cu(II) ions present in aqueous phase. The obtained solid Cu(DDTC)₂ phase was dissolved in chloroform and determined spectrophotometrically at 435 nm. Beer’s law was obeyed over the concentration range of 0.2–5 mg dm⁻³. The molar absorptivity and the Sandell’s sensitivity coefficients of the solutions were 1.0689 × 10⁴ dm³ mol⁻¹ cm⁻¹ and 0.0060 μg cm⁻², respectively. The optimum conditions for each parameter were experimentally determined and possible interferences of various salts were also studied. The method has been validated and applied to determine Cu(II) in various alloys and water samples.     

A luminescent nanosensor for Hg(II) based on functionalized CdSe/ZnS quantum dots

Luminescent and stable CdSe/ZnS core/shell quantum dots (QDs) capped with L-carnitine are firstly prepared for optical determination of mercury ions in ethanol. LC capped QDs have desirable dispersibility, uniformity and good fluorescence properties and were characterized by fluorescence spectroscopy, transmission electron microscopy and infrared spectra. The functionalized QDs turned out to exhibit excellent long-term stability. The modified QDs allowed a highly sensitive determination of mercury ions via analyte-induced changes in the photoluminescence of them. A detection limit of 1.8 × 10⁻⁷ M (36.1 μg · L⁻¹) of mercury ions was obtained, while the interfering effect of other ions (including alkali metal ions, alkali earth metal ions, Ni²⁺, Zn²⁺, Fe²⁺, Ag⁺ and anions such as NO₃ ⁻, SO₄ ²⁻, CO₃ ²⁻ and halogen ions) was negligible even at a very high concentration. The possible mechanism is discussed. Correspondence: Haibing Li, Key Laboratory of Pesticide and Chemical Biology (CCNU), Ministry of Education, College of Chemistry, Central China Normal University, Wuhan 430079, P.R. China; Zhinong Gao, College of Chemistry and Molecular Sciences, Wuhan University, Wuhan 430072, P.R. China     

Determination of glucose by affinity adsorption solid substrate-room temperature phosphorimetry based on concanavalin agglutinin labeled with fluorescein using 1.5-generation dendrimers as sensitizer

In the presence of the heavy atom perturber Pb(Ac)₂, fluorescein (HFin) can emit strong and stable room temperature phosphorescence (RTP) on the surface of a nitrocellulose membrane (NCM) at λ_ex ^max/λ_em ^max = 480/648 nm. It can be spiked with the 1.5-generation polyamidoamine dendrimers (abbreviated: D-1.5) to emit stronger RTP. It was found that a quantitative specific affinity adsorption (AA) reaction between concanavalin agglutinin (abbreviated: Con A) labeled with D-1.5-HFin and N-acetylglucosamine (G) could be carried out on the surface of NCM. The product of the reaction (D-1.5-HFin- Con A-G) could emit strong and stable RTP, and the ΔI_p was proportional to the content of G. According to the above facts, a new method for determination of G by affinity adsorption solid substrate-room temperature phosphorimetry (AA-SS-RTP) was established, based on Con A labeled with fluorescein using D-1.5 dendrimers molecules as sensitizer. The linear range of the sandwich method was 0.040–60 pg G spot⁻¹ (corresponding concentration range: 0.10–150 ng mL⁻¹; sample volume: 0.40 μL spot⁻¹). The regression equation of the working curve was ΔI_p = 6.880 + 5.610 m_G pg spot⁻¹, r = 0.9987. The working solutions containing 0.10 and 150 ng mL⁻¹ G were determined repeatedly 11 times, respectively. The corresponding RSDs were 2.9 and 3.8%. The detection limit of this method calculated by 3Sb/k was 0.021 pg spot⁻¹ (5.2 × 10⁻¹¹ g mL⁻¹). Compared with the direct method (detection limit: 0.078 pg spot⁻¹, linear range: 0.40–40 pg G spot⁻¹), the sensitivity was obviously improved and the linear range was wider. This method has been successfully applied to the determination of G in human plasma, as well as to the supervision and forecast of human diseases, for it is of good sensitivity, accuracy and precision. Correspondence: Jia-Ming Liu, Department of Chemistry and Environmental Science, Zhangzhou Normal College, Zhangzhou 363000, P.R. China     

Fluorometric determination of DNA using nano-SiO2 particles as an effective dispersant and stabilizer for acridine orange

A sensitive fluorometric method for the determination of ctDNA (calf thymus DNA) is presented. It has good selectivity and sensitivity and uses nano-SiO₂ particles as an effective dispersant and stabilizer for acridine orange (AO). Compared to resonance light scattering (RLS) and the conventional method that uses organic dyes as fluorescence probe, the new method is more tolerant towards coexisting foreign substances and also more stable. With 20 mg nano-SiO₂ particles, 10 μmol L⁻¹ AO, at pH 8.01 and an ionic strength of 0.02 mol L⁻¹, the interaction of AO with nano-SiO₂ and ctDNA results in fluorescent signal enhancement. The extent of enhancement was in good proportion to the concentration of ctDNA at excitation/emission wavelengths of 490/523 nm, respectively. The calibration curve was linear over 0.66–55.60 μg mL⁻¹. The determination limit (3σ) was 15 μg mL⁻¹. The method was applied to the determination of ctDNA in synthetic samples with satisfactory results.