分散固相萃取-气相色谱法测定谷物中4种苯甲酸类除草剂EI北大核心CSCD

以新型材料“对甲苯磺酸根-镁铝型水滑石”为分散固相萃取吸附剂,建立了一种同时测定谷物中麦草畏、草灭畏、草芽平和草芽畏4种苯甲酸类除草剂残留量的分散固相萃取-气相色谱法。谷物样品经10%丙酮水溶液涡旋提取、离心,用吸附剂分散固相萃取上清液,经离心、稀硫酸溶解吸附剂、乙醚-乙酸乙酯混合溶液萃取后以三甲基硅基重氮甲烷衍生化,采用气相色谱法测定4种苯甲酸类除草剂,以基质匹配校正曲线外标法定量。结果表明:谷物中4种苯甲酸类除草剂在10~200μg/kg添加水平范围内的平均回收率为84.8%~95.1%,相对标准偏差(RSD)为2.2%~7.2%,方法检出限(LOD)为1.33~3.09μg/kg,定量限(LOQ)为4.42~10.3μg/kg。     

钙离子选择性微电极的研制

研制了有机磷酸盐为活性物质的PVC膜钙离子选择性微电极。电极尖端直径小至4μm,浓度线性范围为10~(-1)-10~(-7)M (10~(-5)M以下采用EDTA体系的金属离子缓冲液配制),检测下限可达2.2×10~(-8)M,选择性系数K~(Pot)Ca,K2.0×10~(-5)、K~(Pot)Ca,Na2.2×10~(-5)、K~(Pot)Ca,Mg2.7×10~(-3),pH适用范围4-10,血清试样中测量游离钙活度的相对标准偏差为4.7％。探讨了影响电极性能的一些因素。曾用该电极测定了某些生理、生化及临床微量试样中的钙离子活度,获得了较好的结果。     

用离子交换法测定低酸度介质中铀酰和L—酒石酸的络合常数

本文用阳离子交换树脂静态法测定了弱酸介质中UO_2~(2+)和L-酒石酸络合物的稳定常數。结果是:离子强度(μ)为0.5,温度在25°、35°、45°、55℃时,β_1分别为2.4×10~(-6)、1.7×10~(-6)、9.1×10~(-7)、5.9×10~(-7);在45°、55℃时,β_2分别为4.7×10~(-9)、7.2×10~(-9);并求得△H(β_1)=-3.8×10~4焦·摩~(-1)。     

三维荧光光谱法连续测定苯胺、二苯胺和N-甲基苯胺

本文比较了苯胺、二苯胺、N-甲基苯胺的二维荧光光谱和三维荧光光谱。提出了同时测定苯胺,二苯胺和N甲基苯胺的分析方法,它们的浓度分别在2.0×10~(-7)～5.0×10~(-6)mol/L,9.0×10~(-8)～7.4×10~(-6)mol/L,1.3×10~(-7)～2.0×10~(-8)mol/L范围内有良好的线性关系,检出限为1.0×10~(-7)mol/L,8.0×10~(-9)mol/L,1.0×10~(-7)mol/L.相对标准偏差分别为5％,7％,7％.此方法用于混合样品和工业废水的分析,获得较满意的结果.     

纯铝中微量钴的极谱测定

钴在1.2×10~(-6)mol·L~(-1)二氮菲-0.02mol·L~(-1)硫脲-6.0×10~(-4)mol·L~(-1)四乙基碘化铵-0.11mol·L~(-1)亚硫酸钠介质(氯化铵-氨水缓冲溶液、pH为9.50)中产生灵敏的极谱催化波;峰电位为-1.68V(vs.SCE),检出限1×10~(-10)mol·L~(-1),钴离子浓度在1×10~(-10)～3×10~(-8)mol·L~(-1)范围内与峰高呈线性关系.体系选择性好,操作简便.用于测定纯铝中1×10~(-7)%以上的钴,重现性好,回收及对照结果满意.     

偶合反应流动注射化学发光法测定汞

基于Hg(Ⅱ)置换Fe(Ⅱ)-DETA配合物中的Fe(Ⅱ)和Fe(Ⅱ)-鲁米诺-溶解氧产生化学发光的反应,建立了置换偶合反应,流动注射化学发光测定痕量汞的新方法.方法线性范围为1×10~(-7)～1×10~(-5)g·ml~(-1)相对标准偏差为3.5%(n=11,C=1×10~(-6)g·ml~(-1)),检出限为3×10~(-8)g·ml~(-1),方法用于工业废水中汞的测定,结果令人满意.     

尿素刀豆生物传感器的研制

本文报告了尿素刀豆生物传感器的制备和性能。斜率46.0—49.7mv.dec~(-1)、线性范围2×10~(-4)—5×10~(-3)mol.L~(-1),检测下限2.5×10~(-5)mol.L~(-1)。该传感器用于血液中尿氮含量的测定,此测定结果与分光光度法测定结果无明显差异。     

生物传感器的研究.V.尿素—石竹花组结电极的研究

尿素—石竹花组织电极是一种植物组织传感器。文中叙述了一种完整石竹花瓣的固定新方法,改善了此类生物传感器的性能:线性范围7.6×10~(-(?))～1.0×10~(-3)mol·L~(-1),斜率47mv·decade~(-1),检测上下限分别为3.2×10~(-3)mol·L~(-1)和4.6×10~(-6)mol·L~(-1),响应时间15～20min,寿命14天.该电极已初步用于实际样品的测定,结果与凯氏法吻合。对尿素含量为3.0×10~(-4)mol·L~(-1)的样品,本法分析结果偏差≤0.2×10~(-4)mol·L~(-1),平均回收率为101.5%(M=3,n=3),表明该传感器具有一定的实用价值。     

TBABr TBAI水溶液体系的电致化学发光的研究

研究了四丁基溴化铵(TBABr)、四丁基碘化铵(TBAI)水溶液体系的电致化学发光。建立了电致化学发光法测定TBABr、TBAI的分析方法。线性范围分别为1.2×10~(-7)～5.0×10~(-5)mol·L~(-1),1.0×10~(-7)～1.5×10~(-5)mol·L~(-1)。检出限为1.0×10~(-7)mol·L~(-1),相对标准偏差均为5％。用该法测定人工合成样品获得较满意的结果。     

银离子选择电极测定矿石中的银

用银离子选择电极测定矿石中的银,文献采用氢溴酸-硫酸蒸煮冒烟的办法消除汞的影响,效果较好。但是,当Ag~+浓度大于10~(-)M时,该方法使测定结果显著偏低。本文试用络合能力较强的乙二胺做为测定银时的离子强度调节剂,操作简便、方法重现性较好。用标准加入法,测定范围为5×10~(-6)～5×10~(-5)M Ag~+;如果用标准样品的pC_(Ag)~+定位,再测量待测样品的pX_(Ag)~+,测定范围为5×10~(-7)～5×10~(-5)M Ag~+。     

Laser-spectroscopic laboratory studies of atmospheric aqueous phase free radical chemistry

Nitrate radical (NO(3)) reactions with benzene (R-1), toluene (R-2), p-xylene (R-3), p-cresol (R-4) and mesitylene (R-5) have been studied by laser photolysis/long path laser absorption (LP-LPLA) in aqueous solution. Rate constants of k(1)=(4.0+/-0.6). 10(8), k(2)=(1.2+/-0.3). 10(9), k(3)=(1.6+/-0.1). 10(9), k(4)= (8.4+/-2.3). 10(8) and k(5)=(1.3+/-0.3). 10(9) lmol(-1)s(-1) were obtained at T=298 K. In addition, reaction rate coefficients for SO(-)(5)+Fe(2+)-->prod. (R-6) and SO(-)(5)+Mn(2+)-->prod. (R-7) of k(6)=(4.3+/-2.4). 10(7) lmol(-1)s(-1) and k(7)=(4.6+/-1.0). 10(6) lmol(-1)s(-1) (T=298 K, I-->0) have been obtained by the application of laser photolysis/UV-VIS broadband diode array spectroscopy. A new laser photolysis/UV-long path laser absorption experiment has been applied to study the reaction of the Cl(-)(2) radical anion with dissolved sulfur(IV). For the reactions Cl(-)(2)+HSO(-)(3)-->2Cl(-)+H(+)+SO(-)(3) (R-8) and Cl(-)(2)+SO(2-)(3)-->2Cl(-)+SO(-)(3) (R-9) rate coefficients of k(8)=(1.7+/-0.2). 10(8) lmol(-1)s(-1) (T=298 K, I-->0) and of k(9)=(6.2+/-0.3). 10(7) lmol(-1)s(-1) (T=279 K, I-->0) were obtained.     

药物在pH敏感聚甲基丙烯酸-poloxamer水凝胶中的扩散行为

平衡溶胀率;药物扩散;药物在pH敏感聚甲基丙烯酸-poloxamer水凝胶中的扩散行为     

CF3CF=CH2 and (Z)-CF3CF=CHF: temperature dependent OH rate coefficients and global warming potentials

Rate coefficients over the temperature range 206-380 K are reported for the gas-phase reaction of OH radicals with 2,3,3,3-tetrafluoropropene (CF(3)CF=CH(2)), k(1)(T), and 1,2,3,3,3-pentafluoropropene ((Z)-CF(3)CF=CHF), k(2)(T), which are major components in proposed substitutes for HFC-134a (CF(3)CFH(2)) in mobile air-conditioning units. Rate coefficients were measured under pseudo-first-order conditions in OH using pulsed-laser photolysis to produce OH and laser-induced fluorescence to detect it. Rate coefficients were found to be independent of pressure between 25 and 600 Torr (He, N(2)). For CF(3)CF=CH(2), the rate coefficients, within the measurement uncertainty, are given by the Arrhenius expression k(1)(T)=(1.26+/-0.11) x 10(-12) exp[(-35+/-10)/T] cm(3) molecule(-1) s(-1) where k(1)(296 K)=(1.12+/-0.09) x 10(-12) cm(3) molecule(-1) s(-1). For (Z)-CF(3)CF=CHF, the rate coefficients are given by the non-Arrhenius expression k(2)(T)=(1.6+/-0.2) x 10(-18)T(2) exp[(655+/-50)/T] cm(3) molecule(-1) s(-1) where k(2)(296 K)=(1.29+/-0.06) x 10(-12) cm(3) molecule(-1) s(-1). Over the temperature range most relevant to the atmosphere, 200-300 K, the Arrhenius expression k(2)(T)=(7.30+/-0.7) x 10(-13) exp[(165+/-20)/T] cm(3) molecule(-1) s(-1) reproduces the measured rate coefficients very well and can be used in atmospheric model calculations. The quoted uncertainties in the rate coefficients are 2sigma (95% confidence interval) and include estimated systematic errors. The global warming potentials for CF(3)CF=CH(2) and (Z)-CF(3)CF=CHF were calculated to be <4.4 and <3.6, respectively, for the 100 year time horizon using infrared absorption cross sections measured in this work, and atmospheric lifetimes of 12 and 10 days that are based solely on OH reactive loss.     

Atmospheric chemistry of CF3CF═CH2 and (Z)-CF3CF═CHF: Cl and NO3 rate coefficients, Cl reaction product yields, and thermochemical calculations

Rate coefficients, k, for the gas-phase reactions of Cl atoms and NO(3) radicals with 2,3,3,3-tetrafluoropropene, CF(3)CF═CH(2) (HFO-1234yf), and 1,2,3,3,3-pentafluoropropene, (Z)-CF(3)CF═CHF (HFO-1225ye), are reported. Cl-atom rate coefficients were measured in the fall-off region as a function of temperature (220-380 K) and pressure (50-630 Torr; N(2), O(2), and synthetic air) using a relative rate method. The measured rate coefficients are well represented by the fall-off parameters k(0)(T) = 6.5 × 10(-28) (T/300)(-6.9) cm(6) molecule(-2) s(-1) and k(∞)(T) = 7.7 × 10(-11) (T/300)(-0.65) cm(3) molecule(-1) s(-1) for CF(3)CF═CH(2) and k(0)(T) = 3 × 10(-27) (T/300)(-6.5) cm(6) molecule(-2) s(-1) and k(∞)(T) = 4.15 × 10(-11) (T/300)(-0.5) cm(3) molecule(-1) s(-1) for (Z)-CF(3)C═CHF with F(c) = 0.6. Reaction product yields were measured in the presence of O(2) to be (98 ± 7)% for CF(3)C(O)F and (61 ± 4)% for HC(O)Cl in the CF(3)CF═CH(2) reaction and (108 ± 8)% for CF(3)C(O)F and (112 ± 8)% for HC(O)F in the (Z)-CF(3)CF═CHF reaction, where the quoted uncertainties are 2σ (95% confidence level) and include estimated systematic errors. NO(3) reaction rate coefficients were determined using absolute and relative rate methods. Absolute measurements yielded upper limits for both reactions between 233 and 353 K, while the relative rate measurements yielded k(3)(295 K) = (2.6 ± 0.25) × 10(-17) cm(3) molecule(-1) s(-1) and k(4)(295 K) = (4.2 ± 0.5) × 10(-18) cm(3) molecule(-1) s(-1) for CF(3)CF═CH(2) and (Z)-CF(3)CF═CHF, respectively. The Cl-atom reaction with CF(3)CF═CH(2) and (Z)-CF(3)CF═CHF leads to decreases in their atmospheric lifetimes and global warming potentials and formation of a chlorine-containing product, HC(O)Cl, for CF(3)CF═CH(2). The NO(3) reaction has been shown to have a negligible impact on the atmospheric lifetimes of CF(3)CF═CH(2) and (Z)-CF(3)CF═CHF. The energetics for the reaction of Cl, NO(3), and OH with CF(3)CF═CH(2) and (Z)-CF(3)CF═CHF in the presence of O(2) were investigated using density functional theory (DFT).     

Effective diffusion coefficients for methanol in sulfuric acid solutions measured by Raman spectroscopy

The diffusion of methanol into 0-96.5 wt % sulfuric acid solutions was followed using Raman spectroscopy. Because methanol reacts to form protonated methanol (CH 3OH 2 (+)) and methyl hydrogen sulfate in H 2SO 4 solutions, the reported diffusion coefficients, D, are effective diffusion coefficients that include all of the methyl species diffusing into H 2SO 4. The method was first verified by measuring D for methanol into water. The value obtained here, D = (1.4 +/- 0.6) x 10 (-5) cm (2)/s, agrees well with values found in the literature. The values of D in 39.2-96.5 wt % H 2SO 4 range from (0.11-0.3) x 10 (-5) cm (2)/s, with the maximum value of D occurring for 61.6 wt % H 2SO 4. The effective diffusion coefficients do not vary systematically with the viscosity of the solutions, suggesting that the speciation of both methanol and sulfuric acid may be important in determining these transport coefficients.     

Nitrogen dioxide multiphase chemistry: uptake kinetics on aqueous solutions containing phenolic compounds

The uptake coefficients of NO2 on aqueous solutions containing guaiacol, syringol and catechol were determined over the pH range from 1 to 13 using the wetted wall flowtube technique. The measured uptake coefficients were used to determine the rate coefficients for the reaction of the physically dissolved NO2 with the neutral and deprotonated forms of phenolic compounds listed above. These organic compounds are ubiquitous not only in biomass burning plumes but also in soils, where they form part of the building blocks of humic acids. The NO2 uptake kinetics on solutions containing guaiacol, syringol or catechol were observed to be strongly pH dependent with uptake coefficients increasing from below 10(-7), under acidic conditions, to more than 10(-5) at pH values above 10. This behaviour illustrates the difference of reactivity between the neutral phenolic species and the phenoxide ions. The corresponding second order rate coefficients were typically observed to increase from 10(5) M(-1) s(-1) for the neutral compounds to a minimum of 10(8) M(-1) s(-1) for the phenoxide ions.     

超高效合相色谱法快速检测纺织品中的8种荧光增白剂

建立了同时检测纺织品中1,2-双(5-甲基-2-苯并恶唑基)-乙烯(PF)、7-二乙氨基-4-甲基香豆素(SWN)、2,2'-(2,5-二苯基硫代)双[5-(1,1-二甲基乙基)]苯并恶唑(OB)、2-[4-[2-[4-(2-苯并恶唑基)苯基]乙烯基]苯基]-5-甲基苯并恶唑(KSN)、1,4-双(2-氰基苯乙烯基)苯(ER-Ⅰ)、1-邻氰苯乙烯基-4-对氰苯乙烯基苯(ER-Ⅱ)、2,2-(1,4-亚萘基)双(苯并恶唑)(KCB)和4,4'-双[2-(2-甲氧基苯基)亚乙基]-1,1'-联苯(FP)8种荧光增白剂的超高效合相色谱(UPC²)检测方法。样品经二甲苯提取、浓缩、定容后,由UPC²进行定性定量分析。以超临界CO₂-甲醇为流动相,梯度洗脱,采用ACQUITY UPC² HSS C18 SB色谱柱(100 mm×3.0 mm,1.8 μm)进行分离。8种荧光增白剂在1.0~20.0 mg/L范围内线性良好(r≥0.9991),定量限(LOQ,S/N=10)在0.70~0.95 mg/L之间。不同添加水平的回收率范围为90.9%~96.5%,相对标准偏差(RSD)为2.8%~4.2%。该方法简单、准确度高、分析时间短,可用于快速检测纺织品中的8种荧光增白剂。     

反相高效液相色谱法对八种吡嗪类化合物保留性能的研究

在Ｓｐｈｅｒｉｓｏｒｂ－Ｃ（１８）反相柱上,以甲醇－水为流动相,对八种吡嗪类化合物的保留性能进行了考察。同时用不同浓度下的冲洗剂所得保留值和关系式ｌｎｋ＇＝ａ＋ｃＣｂ中的参数ａ、ｃ作线性关系,得到很好的相关性。流动相中不同的无机盐及微量有机胺类改性剂的加入,可有效地改进分离。当甲醇：０．２ｍｌ／ＬＨＡｃ－ＮａＡｃ缓冲液（ｐＨ４．５）：三乙胺为４０：５９：１（Ｖ／Ｖ）时,除两种同分异构体不能分离外,所有组分在２５ｍｉｎ内可实现较理想的分离。     

用玻璃电极测定直到15 m的浓盐酸体系的活度系数

本文在25 ℃下, 对0.01844—15.02 mol kg~(-1)浓度范围内的盐酸体系, 用自制Ag|AgGl电极和氢电极, 测定了Harned电池的电动势。在此基础上, 以玻璃电极代替氢电极, 测量上述盐酸体系的电动势, 计算了HCl的平均活度系数和H_2O的活度。实验结果表明, 玻璃电极在浓盐酸体系的“标准电势”是稳定的, 且遵从Nernst响应, 重现性良好, 响应速度快; 在高浓度和稀溶液中交替测量时, 电势无明显偏差。这说明电极有较好的可复性。求得的HCl的活度系数与文献值偏差小于1.2％。玻璃电极的“标准电势”的标准偏差为0.016％。     

Kinetics, mechanism, and thermochemistry of the gas phase reaction of atomic chlorine with dimethyl sulfoxide

A laser flash photolysis-resonance fluorescence technique has been employed to study the kinetics of the reaction of chlorine atoms with dimethyl sulfoxide (CH3S(O)CH3; DMSO) as a function of temperature (270-571 K) and pressure (5-500 Torr) in nitrogen bath gas. At T = 296 K and P > or = 5 Torr, measured rate coefficients increase with increasing pressure. Combining our data with literature values for low-pressure rate coefficients (0.5-3 Torr He) leads to a rate coefficient for the pressure independent H-transfer channel of k1a = 1.45 x 10(-11) cm3 molecule(-1) s(-1) and the following falloff parameters for the pressure-dependent addition channel in N2 bath gas: k(1b,0) = 2.53 x 10(-28) cm6 molecule(-2) s(-1); k(1b,infinity) = 1.17 x 10(-10) cm3 molecule(-1) s(-1), F(c) = 0.503. At the 95% confidence level, both k1a and k1b(P) have estimated accuracies of +/-30%. At T > 430 K, where adduct decomposition is fast enough that only the H-transfer pathway is important, measured rate coefficients are independent of pressure (30-100 Torr N2) and increase with increasing temperature. The following Arrhenius expression adequately describes the temperature dependence of the rate coefficients measured at over the range 438-571 K: k1a = (4.6 +/- 0.4) x 10(-11) exp[-(472 +/- 40)/T) cm3 molecule(-1) s(-1) (uncertainties are 2sigma, precision only). When our data at T > 430 K are combined with values for k1a at temperatures of 273-335 K that are obtained by correcting reported low-pressure rate coefficients from discharge flow studies to remove the contribution from the pressure-dependent channel, the following modified Arrhenius expression best describes the derived temperature dependence: k1a = 1.34 x 10(-15)T(1.40) exp(+383/T) cm3 molecule(-1) s(-1) (273 K < or = T < or = 571 K). At temperatures around 330 K, reversible addition is observed, thus allowing equilibrium constants for Cl-DMSO formation and dissociation to be determined. A third-law analysis of the equilibrium data using structural information obtained from electronic structure calculations leads to the following thermochemical parameters for the association reaction: delta(r)H(o)298 = -72.8 +/- 2.9 kJ mol(-1), deltaH(o)0 = -71.5 +/- 3.3 kJ mol(-1), and delta(r)S(o)298 = -110.6 +/- 4.0 J K(-1) mol(-1). In conjunction with standard enthalpies of formation of Cl and DMSO taken from the literature, the above values for delta(r)H(o) lead to the following values for the standard enthalpy of formation of Cl-DMSO: delta(f)H(o)298 = -102.7 +/- 4.9 kJ mol(-1) and delta(r)H(o)0 = -84.4 +/- 5.8 kJ mol(-1). Uncertainties in the above thermochemical parameters represent estimated accuracy at the 95% confidence level. In agreement with one published theoretical study, electronic structure calculations using density functional theory and G3B3 theory reproduce the experimental adduct bond strength quite well.