386 resultados para HPLC-FLD
em Chinese Academy of Sciences Institutional Repositories Grid Portal
Resumo:
The oligohaline cyanobacterium Aphanizomenon flos-aquae (L.) Ralfs (A. flos-aquae) has been reported in several countries to produce paralytic shellfish poisons (PSPs) or protracted toxic effects. In the past years, A. flos-aquae blooms have occurred annually in the eutrophic Lake Dianchi (300 km(2) in area, located in southwestern China). Material from natural blooms dominated by A. flosaquae was collected and lyophilized. Acute toxicity testing was performed by mouse bioassay using extracts from the lyophilized material. Clear symptoms of PSPs, intoxications were observed. To confirm the production of PSPs, a strain of A. flos-aquae (DC-1) was isolated and maintained in culture. Histopathological effects were studied by examining the organ damages using transmission electron microscopy (TEM). Slight hepatocytic damage with swollen mitochondria was found. The ultrastructural pulmonary lesions were characterized by distortied nuclei and indenting of karyotheca, together with degeneration and tumefaction of mitochondria and endoplasmic reticulum. Control animals injected with acetic acid did not exhibit histopathological damage in any organ. Toxic effects of cultured algal cells on enzymatic systems in the mouse were studied using sublethal doses of extracts. Significant glutathione-S-transferase (GST) and lactate dehydrogenase (LDH) increases, together with decrease of the glutathione (GSH) level, were measured. These results indicated a potential role of PSPs intoxicating and metabolizing in the test animals. HPLC-FLD and LC/MS analysis of extracts from cultured material demonstrated the PSP toxins produced by A. flos-aquae bloom. To the best of our knowledge, this is the first study reporting chemically and toxicologically confirmed PSP toxins related to A. flosaquae in China. (c) 2005 Elsevier Inc. All rights reserved.
Resumo:
Lake Dianchi is in Yunnan Province in southwestern China. In recent years, significant cyanobacterial blooms have occurred in this lake nearly every year because of eutrophication. Monitoring data for the past 5 years acquired by our research group showed that phytoplankton composition alternated between species of Microcystis sp. during warm seasons and those of Aphanizomenon sp. during cool seasons. In March 2003, when phytoplankton composition was highly dominated by Aphanizomenon sp., samples were taken from the lake for toxin detection and immediate strain isolation. A mouse bioassay with extracts from the lyophilized field material showed obvious intoxication from paralytic shellfish poisons (PSPs), and all mice died within 30 min. Further analysis of both field and isolated algal strain Aphanizomenon DC-1 by the postcolumn HPLC-FLD method confirmed its PSP-producing ability The analogues found in the extracts from the field material were neoSTX, dcSTX, and dcGTX3, with contents of 2.279, 1.135, and 0.547 ng/mg DW, respectively. Under laboratory culture condition, toxin content in the Aphanizomenon strain DC-1 varied greatly during different growth phases, with two peaks: in the early-exponential and late-stationary growth phases. When the culture grew at a relatively high rate during the mid- to late-exponential growth phase, toxin content declined gradually. Moreover, the types of toxin in the DC-1 strain varied greatly during a single culture cycle. The HPLC results showed that dcSTX was the only toxin isomer detected throughout the culture period, and its level remained stable. On the other hand, dcGTX2 and GTX4 were the major toxins during the early-exponential and stationary phases, respectively. This article presents the first data on the identification and detection of paralytic shellfish toxins from cyanobacteria in Lake Dianchi. As far as we know, this is also the first report of this type of toxin in inland water bodies in China. Our study indicates the threat associated with PSP toxins in Lake Dianchi and suggests that necessary measures and programs for control are urgently needed to prevent the spread of toxic cyanobacterial blooms. (c) 2006 Wiley Periodicals, Inc.
Resumo:
采用固相微萃取(SPME)高效液相色谱法(HPLC)同时测定了水中苯酚、4-硝基酚、3-甲基酚、2,4-二氯酚、2,4,6-三氯酚、五氯酚等六种酚类化合物的含量.采用ZORBOX SB-C18柱,以甲醇-1%乙酸水溶液为流动相进行梯度洗脱,流速为1.0 mL/min.紫外检测波长为254、280 nm.六种酚类化合物的检出限为0.31~1.90μg/L,加标回收率为88%~103%.该方法操作简单,能快速、准确地检测水中的酚类化合物.
Resumo:
用高效液相色谱 (HPLC)法研究了武汉东湖周年及围隔实验水柱颗粒物色素的组成及变化。共检测到约 2 0种色素 ,类胡萝卜素含量较高的有硅藻的标志色素岩藻黄素 ,隐藻的异黄素 ,蓝、绿藻的黄体素、玉米黄素及胡萝卜素。东湖叶绿素a的代谢产物主要为脱植基叶绿素a(全湖年均约占叶绿素a的 5 % ) ,而非脱镁叶绿素a或脱镁叶绿酸a。围隔实验结果表明 :叶绿素a与总浮游植物 (r =0 .84) ,叶绿素b与绿藻 (r=0 .77) ,岩藻黄素与硅藻 (r =0 6 8) ,异黄素与隐藻生物量 (r=0 .83
Resumo:
The antibacterial drug furazolidone belonging to the group of nitrofuran antibacterial agents has been widely used as an antibacterial and antiprotozoal feed additive for poultry, cattle, and farmed fish in China. During application a large proportion of the administered drug may reach the environment directly or via feces. Although the use of furazolidone is prohibited in numerous countries, there are indications of its illegal use. It is known that furazolidone can be rapidly metabolized to 3-amino-2-oxazolidinone (AOZ) in the body of the target organism. In this study, a total of 21 fish feed samples, including 17 commercial fish feeds from local markets in China (representing 15 different formulations) and 4 fish feeds obtained from Germany and Turkey, respectively, are analyzed to determine whether the drug is still illegally used or commercially available feeds are contaminated by this drug. High-performance liquid chromatography (HPLC) and liquid chromatography-electrospray ionization tandem mass spectrometry (LC-ESI-MS/MS) methods have been implemented to determine furazolidone and its metabolite AOZ in fish feeds containing animal protein, respectively. An efficient and convenient cleanup method for the determination of furazolidone in fish feeds is developed, and a simple cleanup method for the determination of AOZ is used. Method recoveries for samples used were determined as 87.7-98.3% for furazolidone at two spike levels of 2.0 and 5.0 ng g(-1) and as 95.6-102.8% for AOZ at spike levels of 0.4 and 0.8 ng g(-1). Limits of detections were 0.4 ng g(-1) for furazolidone and 0.05 ng g(-1) for AOZ. The established methods are therefore suitable for the determination of furazolidone and its metabolite AOZ in fish feeds at trace contamination levels. Using the established methods, all fish feed samples have been proved to be furazolidone negative; however, AOZ is tested in 16 of 17 fish feeds obtained from local markets in the Hubei province of China, with a positive rate as high as 94.1%.
Resumo:
A simple, rapid and sensitive on-line method for simultaneous determination of four endocrine disruptors (17 beta-estradiol, estriol, bisphenol A and 17 alpha-ethinylestradiol) in environmental waters was developed by coupling in-tube solid-phase microextraction (SPME) to high-performance liquid chromatography (HPLC) with fluorescence detection (FLD). A poly(acrylamide-vinylpyridine-NAP-methylene bisacrylamide) monolith, synthesized inside a polyether ether ketone (PEEK) tube, was selected as the extraction medium. To achieve optimum extraction performance, several parameters were investigated, including extraction flow-rate, extraction time, and pH value, inorganic salt and organic solvent content of the sample matrix. By simply filtered with nylon membrane filter and adjusting the pH of samples to 6.0 with phosphoric acid, the sample solution then could be directly injected into the device for extraction. Low detection limits (S/N = 3) and quantification limits (S/N = 10) of the proposed method were achieved in the range of 0.006-0.10 ng/mL and 0.02-0.35 ng/mL from spiked lake waters, respectively. The calibration curves of four endocrine disruptors showed good linearity ranging from quantification limits to 50 ng/mL with a linear coefficient R-2 value above 0.9913. Good method reproducibility was also found by intra- and inter-day precisions, yielding the RSDs less than 12 and 9.8%, respectively. Finally, the proposed method was successfully applied to the determination of these compounds in several environmental waters. (c) 2006 Elsevier B.V. All rights reserved.
Resumo:
RP-HPLC analysis for low molecular weight organic acids in soil solution has been optimized. An Atlantis (TM) C-18 column was used for the analyses. An optimal determination for eleven organic acids in soil solution was found at room temperature (25 degrees C) and 220 nm detection wavelength, with a mobile phase of 10 mM KH2PO4 -CH3OH (955, pH 2.7), a flow rate of 0.8 mL/min and 10 mu L sample size. The detection limits ranged 3.2-619 ng/mL, the coefficients of variation ranged 1.3-4.6%, and the recoveries ranged 95.6-106.3% for soil solution with standard addition on the optimal conditions proposed.
Resumo:
手性是自然界的一种普遍现象,生命现象离不开手性。手性物质在有机化学、药物化学、生物化学以及功能材料等领域显示出诱人的应用前景。外消旋体的拆分是手性研究的重要基础工作。高效液相色谱手性固定相法(HPLC-CSP)在对映体化合物的分离分析和制备方面表现出独特的优势。本论文以旋光性联萘类聚合物和纤维素类衍生物涂敷的手性固定相进行分析级和半制备级色谱拆分,研究和探讨了它们对外消旋化合物的手性识别能力。1. 纤维素类聚合物的合成 将微晶纤维素与相应的酰氯或异氰酸酯反应获得四种纤维系类衍生物,纤维素三苯甲酸酯(CTB)、纤维素三苯基氨基甲酸酯(CTPC)、纤维素三(3,5-二甲基苯基氨基甲酸酯)(CDMPC)、纤维素三联萘甲酸酯(CTBPT)。红外、核磁、元素分析证明原料纤维素已酯化完全。2. 旋光性聚合物手性固定相及HPLC手性柱的制备采用聚合物涂敷硅胶方法制备了四种纤维素类、三种联萘聚酰胺手性固定相和二种半制备级纤维素手性固定相,匀浆法装柱。研究了不同的涂敷液对色谱柱效的影响。3. 旋光性联萘聚酰胺手性柱拆分能力的探讨 在三种由(S)-联萘聚酰胺涂敷的色谱柱上,以多种流动相体系对多种外消旋化合物进行手性折分试验。4. 纤维素类手性分析柱拆分能力的研究 对手性柱进行塔板数和稳定性测试及拆分能力研究。对一些外消旋化合物实现了手性拆分。由实验结果可以看出,以CDMPC涂敷的手性柱对多种外消旋化合(包括药物)具有手性拆分能力,具分离度较高。5. 半制备级拆分 对三种外消旋药物在纤维素半制备色谱柱上进行了半制备级拆分。我们在分析型色谱柱进行了流动相条件的选择,将优化后的分析条件直接放大到半制备色谱中,不仅节省了模索条件的时间,而且可以节省大量的流动相,预计一天内所能达到的对外消旋体最大拆分量可达克级以上。6. 进行了HPLC-UV-旋光仪的联用检测研究,实现了在线流动过程中旋光曲线的绘制。