同步-导数-化学除氧微乳状液增稳室温磷光法测定痕量荧蒽与屈的研究

同步－导数－化学除氧微乳状液增稳室温磷光法测定痕量荧蒽与屈的研究杨欣,董川,晋卫军,魏雁声,刘长松（山西大学化学系,大原,０３０００６）关键词同步－导致－化学除氧微乳液增稳室温磷光法,荧蒽,屈Ｒａｍｏｓ等［１］于１９８８年提出了微乳状液增稳室温磷光法...     

以滤纸为基质室温磷光法测定痕量多环芳烃的研究

1 前言 固体基质室温磷光法(SS-RTP)是一种发展很快的微量技术与痕量分析相结合的新技术.SS -RTP法以其简便、快速、灵敏的特点在环境污染物及药物分析方面得到了广泛的应用 [1],尤其对于痕量多环芳烃的分析十分有效.文献报道过应用环糊精诱导室温磷光法 [2]和胶束增稳室温磷光法[3]测定的方法.本文用国产快速定量滤纸作固体基质,探讨了测定萘、苊和屈磷光发光的条件,建立了以滤纸为基质的测定痕量萘、苊和屈的SS-RTP法.     

室温磷光分析法的进展与应用

本文对近5年来国内外室温磷光法的研究进展进行了综述,包括固体基质室温磷光、表面活性剂有序介质增稳室温磷光、环糊精诱导室温磷光、敏化和猝灭室温磷光、无保护流体室温磷光、室温磷光化学传感器、生物大分子的室温磷光研究与应用,引用文献158篇.     

卤代萘酐的环糊精诱导室温磷光研究

1 引言。近年来,关于β-环糊精(β-CD)保护下多环芳烃的室温磷光性质已有许多报道,但关于含杂原子的芳环化合物的室温磷光研究较少。从两环芳烃的萘系化合物到多环芳芴和苊等,发光化合物大多为碳环芳烃。卤代1,8-萘酐是重要的有机合成中间体,用作合成DNA光切断剂,抗肿瘤药物、发光材料和荧光分子探针。关于此类物质的室温磷光现象尚未见报道。本实验以Na2SO3为除氧剂,环己烷为空间和匹配作用的第三组分,β-CD为保护性介质,在无外重原子存在下,研究了4-卤代-1,8-萘酐室温磷光发射条件。     

胶束增强荧光法测定6-溴萘硫酸钾

多环芳烃化合物广泛存在于汽车尾气、煤焦油和香烟中,具有致癌作用,国内外对多环芳烃的检测方法研究十分活跃,卤代芳烃则是重要的测试项目之一。文献[1,2]分别报道了环糊精诱导室温磷光法测定β-溴代萘、α-溴代萘,文献[3]报道了室温磷光法测定6-溴萘硫酸钾。本法在十二烷基硫酸钠(SDS)胶束体系中用荧光法测定6-溴萘硫酸钾,与文献方法比较,本法简便、快速,具有一定实用价值。1试验部分1.1仪器与试剂日立F-4500型荧光光度计;pHS-3型酸度计。6-溴萘硫酸钾(BNS)标准溶液:1.0×10-3mol·L-1;十二烷基硫酸钠(SDS)溶液:0.1 mol·L-1;缓冲溶…     

环糊精体系中4种多环芳烃敏化丁二酮室温磷光

对β－环糊精（β－ＣＤ）溶液中４种多环芳烃α－溴代萘（α－ＢｒＮ）、β－溴代萘（β－ＢｒＮ）、菲、Ｑｕ敏化丁二酮（ＢＩＡＣ）的室温磷光（ＲＴＰ）进行了研究，β－ＣＤ能有效地增强敏化磷光强度，并从三重态能量、主客体分子几何尺寸大小等方面讨论了各种因素的影响。方法的线性动态范围上限受能量受体浓度的限制，其检出限达１０＾－８ｍｏｌ／Ｌ。     

以国产微晶纤维素膜作固体基质五种多环芳烃的室温磷光法研究

本文考察了10种国产纤维素膜用于多环芳烃固体基质室温磷光(SS-RTP)的可行性。实验表明:MN-C和MN-P两种型号的微晶纤维素膜用于多环芳烃的SS-RTP是适宜的。阴离子交换纤维素膜、CM-纤维素膜和聚酰胺-6膜也能诱导出多环芳烃的RTP来,但其性能逊于前两种。故本文应用MN-C和MN-P两种微晶纤维素膜基质考察了五种多环芳烃的RTP特征,并建立了它们的SS-RTP新方法。并与用滤纸作基质的实验结果进行了比较,表明两种新的固体基质的RTP性能优于滤纸基质。     

离子交换树脂增稳的室温磷光特性及分析应用研究

本文研究了7-碘-8-羟基喹啉-5-磺酸及8-羟基喹啉-5- 磺酸同金属离子形成的配合物在水溶液中被阴离子交换树脂吸附后所表现出来的室温磷光特性. 制作了测定Al^3^+,Ga^3^+,In^3^+,Zr^4^+和Hf^4^+等金属离子的室温磷光传感器.实验结果表明:离子交换树脂增稳的室温磷光对湿气不敏感,选择性高, 可用于发展一类新型的金属离子传感器     

多环芳烃混合物的快速导数-恒能量同步荧光光谱分析

多环芳烃混合物的快速导数-恒能量同步荧光光谱分析;导数技术     

偏振—导数—同步荧光法同时测定痕量芴,苊,蒽,北

本文采取偏振－导数－同步扫描联用技术同时测定痕量的芴、苊、恩和北多环芳烃。实验结果表明，多种荧光分析技术联用可以弥补单独应用其中一种或两种技术的不足，扬长避短，大大改善此类化合物的检测限。该方法同时测定上述四种组份，检测限依次为０．０８９、２．４、０．０４５、０．００９６ｎｇ／ｍＬ，相对标准偏差不大于５％。     

Resolution of 13 polycyclic aromatic hydrocarbons by constant-wavelength synchronous spectrofluorometry.

A method capable of determining 13 PAHs (acenaphthene, anthracene, benzo[a]anthracene, benzo[a]pyrene, benzo[b]fluoranthene, benzo[k]fluoranthene, chrysene, dibenzo[ah]anthracene, fluoranthene, fluorene, indene[1,2,3-cd]pyrene, phenanthrene and pyrene) in a mixture of 16 EPA PAHs by second derivative synchronous spectrofluorometry in the constant wavelength mode was developed. It has not been possible to determine the following PAHs in the mixture: acenaphthylene, benzo[ghi]perylene and naphthalene. The approach studied allows the sensitive, rapid and inexpensive identification and quantitation of 13 PAHs in a solution of hexane. The detection limits are <1 microg L(-1) (except for chrysene and phenanthrene).     

高效液相色谱分离偏振同步荧光同时检测环境样品中的茐、苊、 、苯并[a]荧蒽

以高效液相色谱（ＨＰＬＣ）为分离手段，偏振同步荧光法为检测手段，实现了环境样 品中茐、苊、　、苯并[a]荧蒽（Ｂ［ａ］Ａ）的同时检测。所建方法对茐、苊、　、Ｂ[a]Ａ的检测限分 别为 ０．０３９，０．０４６，０．０１６和 ０．０４２（ｍｇ／Ｌ）。该法用于大气、海洋沉积物中的茐、苊、　、Ｂ[a] Ａ的同时测定，结果满意。     

Solid-surface phosphorescence characterization of polycyclic aromatic hydrocarbons and selective determination of benzo(a)pyrene in water samples

This paper presents the phosphorescence characterization of polycyclic aromatic hydrocarbons (PAHs) on solid-surface for obtaining new flow-through phosphorescence optosensors for PAHs-based on-line, immobilized onto a non-ionic resin solid support coupled to a continuous flow system and the applications for the selective determination of benzo(a)pyrene (BaP). The phosphorescent characterization of 15 PAHs, described as major pollutants by the Environmental Protection Agency (EPA) (naphthalene, acenaphthylene, acenaphthene, fluorene, phenanthrene, anthracene, fluoranthene, pyrene, chrysene, benzo(a)anthracene, benzo(k)fluoranthene, benzo(b)fluoranthene, benzo(a)pyrene, indeno(1,2,3-cd)pyrene, benzo(g,h,i)perylene and dibenzo(a,h)anthracene) has been carried out. The experimental variables (heavy atom, deoxygenation and organic solvent in samples) for obtaining different possibilities for developing mono and multi-parameter PAH sensors and the conditions for PAH screening have been carefully studied and the experimental conditions to determination of BaP in presence of other PAHs in water samples have been optimized.     

New approach for screening polycyclic aromatic hydrocarbons in water samples

For the first time, solid-phase extraction (SPE) has been combined to room-temperature phosphorimetry (RTP) to determine the 16 polycylic aromatic hydrocarbons related as major pollutants by the US Environmental Protection Agency (EPA). These include naphthalene, anthracene, acenaphthylene, acenaphthene, fluorene, fluoranthene, benzo(a)anthracene, benzo(k)fluoranthene, benzo(b)fluoranthene, benzo(a)pyrene, indeno(1,2,3-cd)pyrene, pyrene, chrysene, phenanthrene, benzo(g,h,i)perylene and dibenzo(a,h)anthracene. The pre-concentration factor obtained by SPE, combined with the sensitivity of RTP, resulted in calibration curves with linear dynamic ranges at the parts-per-billion level (ng ml(-1)). The limits of detection were estimated at the parts-per-trillion level (pg ml(-1)). Several pollutants usually encountered in water samples were tested for interference. These included polychlorinated biphenyls, pesticides, and volatile organic compounds. As a result of the appropriate combination of excitation wavelength (330 nm) and phosphorescence enhancers (0.1 M TlNO(3) and 0.05 M sodium dodecyl sulfate, SDS), no interference was observed. The results demonstrate the potential of SPE-RTP for screening polycyclic aromatic hydrocarbons (PAHs) in environmental waters.     

Determination of Heavy Polycyclic Aromatic Hydrocarbons (PAH) in Drinking Water,Ambient Air,Soils, Sediments and Food Stuffs by HPLC Method with Fluorescence Detection

The methods for the determination of some heavy PAH in different objects by HPLC method with fluorescence detection have been developed. The following conditions for the separation of PAH have been chosen:The column 150 mm length, internal diameter 2.1 mm filled by reversible-phase sorbent Zorbax ODS (5 μ),mobile phase acetonutrile/water (80:20), the injected volume of sample concentrate 10 μ L, the velocity of mobile phase 200 μ L.min. The excitation region is 290-300 nm, the emission one is 350-420 nm. Under condition chosen the limit of detection are 5 pg for benz(a)pyrene,10 pg for pyrene and chrysene3 pg for benz(k)fluoranthene, and 20 pg for anthracene. The dynamic range is 3 order of magnitude. The reproducibility of peak highs is better than 5%.     

The development of solid-surface fluorescence characterization of polycyclic aromatic hydrocarbons for potential screening tests in environmental samples

This paper presents the characterization of polycyclic aromatic hydrocarbons (PAHs) in solid-surface fluorescence as the first step for obtaining new optical sensors for PAHs screening. The fluorescence properties of the EPA-PAHs (naphthalene, acenaphthene, acenaphthylene, fluorene, phenanthrene, anthracene, fluoranthene, pyrene, chrysene, benzo[a]anthracene, benzo[k]fluoranthene, benzo[b]fluoranthene, benzo[a]pyrene, indeno [1,2,3-cd]pyrene, benzo[g,h,i]perylene and dibenzo[a,h]anthracene) on five types of solid-surfaces were evaluated. The experimental variables (pH and percentage of organic solvent in samples) were studied, obtaining different possibilities for making individual sensors for some of these PAHs and the best conditions for developing sensors for PAH screening were also studied.     

Validation of a method for extraction of polycyclic aromatic hydrocarbons from sewage sludge and analysis by GC-MS

In the present study, the solid–liquid extraction with low temperature purification was validated for the determination of 16 polycyclic aromatic hydrocarbons from sewage sludge by gas chromatography-mass spectrometry. Recoveries ranged 70–114% for naphthalene, acenaphthylene, acenaphthene, fluorene, phenanthrene, anthracene, fluoranthene, pyrene, benzo[a]anthracene and chrysene, while the compounds benzo[b]fluoranthene, benzo[k]fluoranthene, benzo[a]pyrene, indeno[1,2,3-cd]pyrene, dibenzo[a,h]anthracene and benzo[g,h,i]perylene showed recoveries of between 40 and 70%. The relative standard deviation was less than 13% for all of the compounds. Negative matrix effect was observed on the 10 compounds with less retention time in the chromatographic analysis and positive matrix effect noticed on the others. The limits of quantification were from 2 to 20 μg kg^?1, about 30 times less than the maximum residue limit allowed in sludge by the European Union. The validated method produced quantification of 11 PAHs in one sludge sample at concentrations ranging 20–2000 μg kg^?1.     

Determination of polycyclic aromatic hydrocarbons in Athens atmosphere

Concentrations of total suspended particulates (TSP), benzene soluble fraction (BSF) and polycyclic aromatic hydrocarbons (PAH) have been determined in ambient air from four different sites in Athens, situated in urban, semi-industrial and industrial areas. GLC analysis has been applied for the determination of PAH, while the CGC/MS technique was used in order to confirm the obtained results. The same PAH pattern was observed for all stations. The identified PAH have been fluoranthene (FLA), pyrene (PYR), benzo(a)anthracene (BaA), chrysene (CHR), benzo(b)fluoranthene (BbF), benzo(k)fluoranthene (BkF), benzo(a)pyrene (BaP), benzo(e)pyrene (BeP) and benzo(ghi)perylene (B(ghi)P). The concentrations of individual PAH ranged from traces to 33 ng m-3 (e.g. same or lower comparing to other large cities). The higher values of PAH were found during adverse meteorological conditions.     

Supercritical fluid extraction of polycyclic aromatic hydrocarbons from liver samples and determination by HPLC-FL

An extraction/clean-up procedure by SFE was developed for isolating PAHs from liver samples for subsequent HPLC-FL determination of ten PAHs in the enriched extract. Recoveries (90-115%) and RSD % (< or =7.7) were satisfactory. When applied to 11 samples of bird of prey (Tyto alba) protected species and classified of special interest, from the Galicia (Northwest to Spain), benzo[ghi]perylene and indeno[1,2,3-cd]pyrene were undetectable; chrysene and benzo[a]pyrene are only detected in one sample; benzo[a]anthracene and benzo[k]fluoranthene are only quantified in one sample and benzo[b]fluoranthene in two samples. The other PAHs, anthracene, fluoranthene and pyrene are present in almost all the samples.