枢复宁在肺癌患者体内的药物动力学和生物利用度

９名接受顺铂化疗的原发性肺癌患者单次口服和静脉注射枢复宁８ｍｇ后，用反相高效液相色谱法测定血浆药物浓度。经用ＰＫＢＰ－Ｎ１程序在计算机上拟合计算表明，枢复宁在人体内表现为二房室模型。口服后主要药动学参数：Ｔ１／２Ｋａ＝０．４１±０．３０ｈ，Ｔ１／２α＝０．９±０．４３ｈ，Ｔ１／２β＝３．３±１．２ｈ，Ｃｍａｘ＝２８．６±９．５ｎｇ／ｍｌ，Ｔｍａｘ＝１．７±０．９ｈ，ＡＵＣ＝１５８±７３ｎｇ·ｈ／ｍｌ，绝对生物利用度为５５％。     

盐酸特拉唑嗪胶囊人体生物利用度及药物动力学研究

目的：对盐酸特拉唑嗪胶囊的人体内生物利用度进行研究。方法：单剂量口服盐酸特拉唑嗪胶囊和片剂２ｍｇ。血药浓度采用ＨＰＬＣ测定，数据用３Ｐ８７计算药动学参数。结果：盐酸特拉唑嗪胶囊剂的药动学参数：Ｋａ为８．２±４．０ｈ－１，Ｔ１／２为８．２±２．５ｈ，Ｔｍａｘ为０．６１±０．１１ｈ，Ｃｍａｘ为４３．５±８．５ｎｇ·ｍｌ－１，ＡＵＣ为３６７．４±３４．６ｎｇ·ｈ·ｍｌ－１；盐酸特拉唑嗪片剂的药动学参数：Ｋａ为６．４±７．４ｈ－１，Ｔ１／２为７．４±２．１ｈ，Ｔｍａｘ为０．９±０．４ｈ，Ｃｍａｘ为４３．１±４．８ｎｇ·ｍｌ－１，ＡＵＣ为３７１．３±４４．４ｎｇ·ｈ·ｍｌ－１。结论：两种剂型的药物动力学参数之间差异均无显著性（Ｐ＞０．０５），胶囊剂的相对生物利用度为９９．８８％。     

盐酸伪麻黄碱在人体中的药物动力学

采用反相高效液相色谱外标法测定人血清中伪麻黄碱浓度，并测定８例志愿受试者伪麻黄碱血药浓度，并计算分析药物动力学参数，结果单剂量口服９０ｍｇ盐酸伪麻黄碱后，药时曲线呈一室模型。Ｔｍａｘ＝１．７±１．１ｈ，Ｃｍａｘ＝３６４±９４ｎｇ·ｍｌ－１，ＡＵＣ（０～∞）＝２６６２±３０３（ｎｇ·ｈ·ｍｌ－１），Ｔ１／２＝４．０±１．０ｈ，Ｋａ＝２．４±１．４ｈ－１，Ｋｅ＝０．１９±０．０４ｈ－１，Ｖｄ＝０．１９±０．０５ｍｇ，Ｃｌ＝０．０３±０．０１ｍｇ·ｈ－１。     

新型双氯芬酸钠缓释片的人体相对生物利用度研究

８名健康男性志愿者单剂量交叉口服１００ｍｇ受试双氯芬酸钠缓释片、扶他林或ＶｏｌｔａｒｅｎＳＲ１００后,Ｔｍａｘ分别为２．４±１．０、２．１±０．５和４．４±１．８ｈ;Ｃｍａｘ分别为６０２．６±９２．８、３３３７．６±１０８８．２　７６１．０±３４２．０ｎｇ／ｍｌ;ＭＲＴ分别为１３．２±４．８、２．９±０．８和７．９±１．９ｈ;ＡＵＣ０分别为４８６６．２±６４４．６、５３１４．３±５３４．３和４８２９．１±５８２．８ｎｇ／（ｍｌ－１·ｈ）;双氯芬酸钠缓释片和ＶｏｌｔａｒｅｎＳＲ１００相对于扶他林的生物利用度分别为８８．３±１３．２％和８６．３±１２．６％。另８名志愿者交叉口服受试双氯芬酸钠缓释片（１００ｍｇ,ｐｄ）和扶他林（５０ｍｇ,ｂｉｄ〕,连服５天。Ｃｍａｘ分别为５９３．９±１３４．１、１２４７．８±５２７．５ｎｇ／ｍｌ,峰谷波动率（ＰＴＦ）分别为３．３±１．２、５．３±２．１。本研究将为新型双氯芬酸钠缓释片的临床应用提供依据。     

双氯灭痛在正常人体内的药物动力学研究

采用反相高效液相色谱法测定了１０例健康人单剂量口服７５ｍｇ双氯灭痛片剂后血浆药浓度，研究了该药物在中国人体内药物动力学。经用ＰＫＢＰ－Ｎ＿１程序包在计算机上拟合计算表明，双氯灭痛口服给药多数人表现为二房室模型。其主要药动学参数分别为：Ｔ＿（α１／２）＝０．４０±０．１１ｈ，Ｔ＿（β１／２）＝１．７７±０．５ｈ，Ｔ＿（ｍａｘ）＝１．７８±０．３２ｈ，Ｃ＿（ｍａｘ）＝１．８７±０．９μｇ／ｍｌ，ＡＵＣ＝３．８１±１．７μｇ／（ｍｌ·ｈ）。结果表明，中国人体内的药动学参数与所报道的外国人体内相似。     

阿莫西林和克拉维酸钾复合制剂的药物动力学

本文对阿莫西林－克拉维酸钾复合制剂在９名健康成人中进行药物代谢动力学和生物利用度研究。血浆中药物浓度分别用藤黄八叠球菌和克雷伯氏肺炎杆菌为检定菌（用井式琼脂平板法）测定阿莫西林和克拉维田钾。单剂量口服２５０ｍｇ阿莫西林和１２５ｍｇ克拉维酸钾后其阿莫西林的Ｔｍａｘ１．１７±０．３１ｈｆｏ０．９７±０．３３ｈ；Ｃｍａｘ３．５±０．６μｇ／ｍｌ和３．６±０．７μｇｍｌ；Ｔ１／２１．１±０．３ｈ和１．１５±０．２７ｈ。克拉维酸钾为：Ｔｍａｘ１．ｌｌ±０．２４ｈ和０．８９±０．２９ｈ；Ｃｍａｘ３．６±１．０μｇ／ｍｌ和４．０±１．４４μｇ／ｍｌ；Ｔ１／２０．７８±０．１９ｈ和０．８±０．４ｈ。颗粒剂的相对生物利用度阿莫西林为１０４±２０％，克拉维酸钾为１０８±１１％。     

高效液相色谱法测定人血清中西替利嗪及其药动力学

目的：建立高效液相色谱法测定人血清中西替利嗪。方法：用ＨＰＬＣ法检测８名健康自愿者血中西替利嗪浓度,经３Ｐ８７程序拟合,计算药动学参数。结果：西替利嗪药动学参数Ｔ１／２ａ,Ｔ１／２β,Ｔｍａｘ,Ｃｍａｘ,Ｖ／Ｆ和ＡＵＣ分别为（１．６±０．８）ｈ,（７．２±１．１）ｈ,（１．３±０．４）ｈ,（３７４．７±６１．８）ｎｇ．ｍｌ＾－１,（３９．１±８．８）Ｌ和（３１８８．４±２４６．１）ｎｇ．ｈ．ｍｌ＾     

羟乙桂胺在肌肉挛缩患者及健康志愿者体内的药物动力学

９名肌肉挛缩患者和６名健康志愿者口服羟乙桂胺片１５ｍｇ／ｋｇ，用ＨＰＬＣ测定血药浓度并计算动力学参数。９名肌肉挛缩患者口服后的达峰时间Ｔｍａｘ（约１ｈ），峰浓度Ｃｍａｘ（５．５±０．８μｇ／ｍｌ）；ｋａ（１．１９±０．１４ｈ－１），ｔ１／２α（１．０８±０．３１ｈ），ｔ１／２β（３．３７±１．０５ｈ），与健康志愿者无显著差异（ｐ＞０．０５）。     

口服茶碱缓释胶囊的药物动力学

采用荧光偏振免疫法（ＦＰＩＡ），对１２名老年慢性阻塞性肺病（ＣＯＰＤ）患者口服单剂量和多剂量茶碱缓释胶囊（ＰＴ）测定经时血药浓度并计算药物动力学参数。结果表明，单剂量组口服ＰＴ后Ｔｍａｘ＝７．０±６．０ｈ，Ｃｍａｘ＝６．８±２．６ｍｇ·Ｌ－１；多剂量组连续口服ＰＴ后Ｔｓｓｍａｘ＝４．０±１．８ｈ，Ｃｓｓｍａｘ＝１６．５±２．６ｍｇ·Ｌ－１。     

进口和国产索他洛尔片剂的相对生物利用度研究

目的：本文对进口和国产索他洛尔片剂在１２名男性健康志愿者中的药物动力学和相对生物利用度进行了研究。方法：建立了一个检测血清中索他洛尔浓度的反相高效液相色谱－荧光检测法。结果：单剂量口服索他洛尔１６０ｍｇ后的血药浓度数据用３Ｐ８７药物动力学程序进行模型拟合，国产片剂ＡＵＣ、Ｃｍａｘ、Ｔｍａｘ、Ｔ１／２分别为１６．２±３．６ｈ·μｇ·ｍｌ－１，１．２±０．２μｇ·ｍｌ－１，２．１±０．７ｈ，１７．０±７．２ｈ；进口片剂ＡＵＣ、Ｃｍａｘ、Ｔｍａｘ、Ｔ１／２分别为１５．９±３．５ｈ·μｇ·ｍｌ－１，１．２±０．４μｇ·ｍｌ－１，２．１±０．６ｈ，１８．６±９．４ｈ。国产片剂的相对生物利用度为１０３．５％。结论：两种片剂的所有药动学参数经统计学（ＳＰＳＳ软件）处理差异均无显著性（Ｐ＞０．０５）。     

Efficacy of gut lavage,hemodialysis, and hemoperfusion in the therapy of paraquat or diquat intoxication

Clinical and in vitro investigations were carried out to test the efficacy of gut lavage, hemodialysis, and hemoperfusion in the treatment of poisoning with paraquat or diquat. In a patient suffering from diquat intoxication 130 times more diquat was removed by gut lavage 30 h after ingestion than was removed by complete aspiration of the gastric contents.Determination of in vitro clearances for paraquat and diquat by hemodialysis showed that, at serum concentrations of 1–2 ppm, such as are frequently encountered in poisoning in man, toxicologically relevant quantities of herbicide cannot be removed from the body. At a concentration of 20 ppm, on the other hand, hemodialysis proved to be effective, the clearance being 70 ml/min at a blood flow rate of 100 ml/min. The efficacy of hemoperfusion with coated activated charcoal was on the whole better. Especially at concentrations around 1–2 ppm, the clearance values for hemoperfusion were some 5–7 times higher than those for hemodialysis.In a patient suffering from paraquat poisoning, both hemodialysis as well as hemoperfusion were carried out. The in vitro results could be confirmed: At serum concentrations of paraquat less than 1 ppm no clearance could be obtained by hemodialysis while by hemoperfusion with activated charcoal quite high clearance values were measured and the serum level dropped down to zero.

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Zusammenfassung Klinische Untersuchungen und Laboratoriumsversuche wurden durchgeführt, um die Wirksamkeit von Darmspülung, Hämodialyse und Hämoperfusion bei Paraquat- und Deiquat-Vergiftungen zu prüfen.Bei einem Patienten wurde 30 Std nach Deiquat-Aufnahme durch Darmspülung 130mal mehr Deiquat entfernt als durch vollständige Aspiration des Mageninhaltes. In vitro-Versuche ergaben, daß bei Blutserumkonzentrationen von 1–2 ppm, die bei Vergiftungen oft gemessen werden, durch Hämodialyse keine toxikologisch relevanten Paraquat- oder Deiquat-Mengen entfernt werden können. Dagegen erwies sich die Hämodialyse bei 20 ppm und einer Blutumlaufgeschwindigkeit von 100 ml/min mit einer Clearance von 70 ml/min als wirksam. Die Hämoperfusion mit beschicheter Aktivkohle war in diesen Versuchen aber eindeutig überlegen, denn insbesondere bei Konzentrationen um 1–2 ppm waren die Clearance-Werte 5–7mal höher als bei der Hämodialyse.Die in vitro-Ergebnisse wurden bei einem Patienten mit einer Paraquat-Vergiftung bestätigt: Bei Konzentrationen unter 1 ppm war die Hämodialyse wirkungslos, während durch Hämoperfusion relativ hohe Clearance-Werte erreicht wurden, so daß der Serumspiegel rasch unter die Nachweisgrenze abfiel.

     

In vitro studies on sterically stabilized liposomes (SL) as enzyme carriers in organophosphorus (OP) antagonism

This study describes a new approach for organophosphorous (OP) antidotal treatment by encapsulating an OP hydrolyzing enzyme, OPA anhydrolase (OPAA), within sterically stabilized liposomes. The recombinant OPAA enzyme was derived from Alteromonas strain JD6. It has broad substrate specificity to a wide range of OP compounds: DFP and the nerve agents, soman and sarin. Liposomes encapsulating OPAA (SL)* were made by mechanical dispersion method. Hydrolysis of DFP by (SL)* was measured by following an increase of fluoride ion concentration using a fluoride ion selective electrode. OPAA entrapped in the carrier liposomes rapidly hydrolyze DFP, with the rate of DFP hydrolysis directly proportional to the amount of (SL)* added to the solution. Liposomal carriers containing no enzyme did not hydrolyze DFP. The reaction was linear and the rate of hydrolysis was first order in the substrate. This enzyme carrier system serves as a biodegradable protective environment for the recombinant OP-metabolizing enzyme, OPAA, resulting in prolongation of enzymatic concentration in the body. These studies suggest that the protection of OP intoxication can be strikingly enhanced by adding OPAA encapsulated within (SL)* to pralidoxime and atropine.     

Steroidal sapogenin contents in some domestic plants

In order to find out the values of the steroid resources for the future use. the compositions and contents of steroidal sapogenins from 13 domestic plants have been investigated. As a result,Dioscorea nipponica, D. quinqueloba andSmilax china were found to have large amount of diosgenin. And pennogenin inTrillium kamtschaticum andParis verticillata, yuccagenin inAllium fistulosum, hecogenin inAgave americana and neochlorogenin inSolanum nigum were appeared to be major steroidal sapogenins.     

Synthesis,Cytotoxicity and Antileishmanial Activity of Some N-(2-(indol-3-yl)ethyl)-7-chloroquinolin-4-amines

We report herein the condensation of 4,7-dichloroquinoline (1) with tryptamine (2) and D-tryptophan methyl ester (3) . Hydrolysis of the methyl ester adduct (5) yielded the free acid (6) . The compounds were evaluated in vitro for activity against four different species of Leishmania promastigote forms and for cytotoxic activity against Kb and Vero cells. Compound (5) showed good activity against the Leishmania species tested, while all three compounds displayed moderate activity in both Kb and Vero cells.     

Aquatic Insects and Trace Metals: Bioavailability,Bioaccumulation, and Toxicity

Abstract

The uptake of metals from food and water sources by insects is thought to be additive. For a given metal, the proportions taken up from water and food will depend both on the bioavailable concentration of the metal associated with each source and the mechanism and rate by which the metal enters the insect. Attempts to correlate insect trace metal concentrations with the trophic level of insects should be made with a knowledge of the feeding relationships of the individual taxa concerned. Pathways for the uptake of essential metals, such as copper and zinc, exist at the cellular level, and other nonessential metals, such as cadmium, also appear to enter via these routes. Within cells, trace metals can be bound to proteins or stored in granules. The internal distribution of metals among body tissues is very heterogeneous, and distribution patterns tend to be both metal and taxon specific. Trace metals associated with insects can be both bound on the surface of their chitinous exoskeleton and incorporated into body tissues. The quantities of trace meals accumulated by an individual reflect the net balance between the rate of metal influx from both dissolved and particulate sources and the rate of metal efflux from the organism. The toxicity of metals has been demonstrated at all levels of biological organization: cell, tissue, individual, population, and community. Much of the literature pertaining to the toxic effects of metals on aquatic insects is based on laboratory observations and, as such, it is difficult to extrapolate the data to insects in nature. The few experimental studies in nature suggest that trace metal contaminants can affect both the distribution and the abundance of aquatic insects. Insects have a largely unexploited potential as biomonitors of metal contamination in nature. A better understanding of the physico-chemical and biological mechanisms mediating trace metal bioavailability and exchange will facilitate the development of general predictive models relating trace metal concentrations in insects to those in their environment. Such models will facilitate the use of insects as contaminant biomonitors.