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1.
目的:评价受试制剂甲苯磺酸妥舒沙星分散片与参比制剂甲苯磺酸妥舒沙星片在中国健康人体内的生物等效性。方法:入选18名男性健康志愿者,随机交叉单剂量口服甲苯磺酸妥舒沙星分散片或甲苯磺酸妥舒沙星片0.3 g,HPLC法测定血浆中妥舒沙星浓度。经DAS 2.0药代动力学计算程序处理参数,并进行双单侧t检验确定是否生物等效。结果:甲苯磺酸妥舒沙星分散片和甲苯磺酸妥舒沙星片的药动学参数分别如下:t1/2分别为(5.17±1.96)和(5.13±2.10)h;tmax分别为(0.89±0.19)和(0.86±0.20)h;Cmax分别为(0.53±0.09)和(0.51±0.09)μg/mL;AUC0-24 h分别为(1.75±0.67)和(1.76±0.66)μg.h.mL-1;AUC0→∞分别为(1.98±0.74)和(1.98±0.76)μg.h.mL-1。甲苯磺酸妥舒沙星分散片受试制剂相对于参比制剂的相对生物利用度F为(101.1±15.6)%。结论:经统计学分析,受试制剂甲苯磺酸妥舒沙星分散片与参比制剂甲苯磺酸妥舒沙星片具有生物等效性。  相似文献   

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国产妥舒沙星临床药物动力学   总被引:7,自引:0,他引:7  
目的研究国产妥舒沙星在健康志愿者中的体内过程。方法8名受试者随机交叉空腹口服国产和进口妥舒沙星片剂300mg,以HPLC法测定血、尿药物浓度。结果受试者单次空腹口服妥舒沙星片后体内过程均符合一室模型,平均cmax分别为0.626和0.627mg/L,tmax分别为1.12和1.30h,t1/2ke分别为4.42和4.37h,AUC分别为4.47和4.65h*mg/L,原药24h尿累积排出率分别为22.18%和22.34%。结论受试者单剂空腹口服国产妥舒沙星片剂后体内过程和进口品相仿。  相似文献   

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目的评价国产(受试制剂)及进口(参比制剂)吉米沙星片在中国健康人体内的生物等效性。方法 22名男性健康受试者采用随机交叉设计试验,用高效液相色谱-紫外检测(HPLC-UV)法测定单剂量口服吉米沙星片受试制剂和参比制剂各320 mg后吉米沙星的血药质量浓度。所得数据经WinNonlin4.2药动学计算程序处理计算主要药动学参数,并进行双单侧t检验确定是否生物等效。结果吉米沙星参比制剂与受试制剂主要药动学参数:tmax分别为(1.1±0.4)h和(1.0±0.5)h;ρmax分别为(2.39±0.58)mg·L-1及(2.54±0.76)mg·L-1;t1/2分别为(7.2±1.2)h及(7.5±1.6)h;AUC0-36 h分别为(12.88±2.29)mg·h·L-1和(13.07±2.83)mg·h·L-1;AUC0-∞分别为(13.57±2.32)mg·h·L-1和(13.82±2.87)mg·h·L-1;吉米沙星片受试制剂相对于参比制剂的生物利用度为(102.5±17.9)%,统计学结果表明受试制剂与参比制剂的tmax、ρmax、t1/2、AUC均无显著差异(P>0.05)。结论本文HPLC-UV法样品处理简便迅速,方法灵敏度高,可准确测定吉米沙星血药浓度。测定的国产吉米沙星片与进口品具有生物等效性。  相似文献   

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目的建立HPLC内标法测定血浆中司帕沙星含量,并研究司帕沙星片的相对生物利用度及生物等效性。方法 20名健康志愿者分2组,随机、交叉口服试验制剂与参比制剂的司帕沙星片0.4 g,测定其血药浓度,计算药物动力学参数及生物等效性评价。结果试验制剂与参比制剂血浆中司帕沙星的tmax为(4.68±0.44)和(4.55±0.51)h;Cmax为(1 560.4±243.9)和(1 584.1±273.9)ng.mL-1;t1/2为(20.92±4.85)和(19.81±3.75)h;用梯形法计算AUC0-t为(43 325±12 174)和(44 139±11 815)ng.h.mL-1;AUC0-∞为(45 452±12 884)和(45 999±12 629)ng.h.mL-1。以AUC0-t计算,试验制剂的平均相对生物利用度为(97.9±5.8)%。结论该法操作简便,快速灵敏,可用于测定血浆中的司帕沙星浓度;司帕沙星的两制剂具有生物等效性。  相似文献   

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目的建立测定血浆中司帕沙星的HPLC内标法并研究司帕沙星片的相对生物利用度及生物等效性。方法 20名健康志愿者分两组,随机、交叉口服受试制剂与参比制剂的司帕沙星片0.4 g,HPLC法测定血药浓度,计算药动学参数及生物等效性评价。结果受试制剂与参比制剂血浆中司帕沙星的tmax为(4.68±0.44)和(4.55±0.51)h;Cmax为(1 560.4±243.9)和(1 584.1±273.9)ng/ml;t1/2为(20.92±4.85)和(19.81±3.75)h;用梯形法计算AUC0-t为(43 325±12 174)和(44 139±11 815)ng.h/ml;AUC0-∞为(45 452±12 884)和(45 999±12 629)ng.h/ml。以AUC0-t计算,受试制剂的平均相对生物利用度为(97.9±5.8)%。结论两制剂具有生物等效性。  相似文献   

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国产与进口奥氮平片的人体药动学及生物等效性   总被引:5,自引:0,他引:5  
目的:考察健康受试者口服奥氮平片的药动学,比较国产制剂与进口制剂的生物等效性.方法:采用双周期两制剂交叉试验设计,22例男性健康志愿者随机分为2组,交叉单次剂量口服国产或进口奥氮平片10mg,用高效液相色谱电化学检测法测定给药后不同时间点血浆中奥氮平的浓度,采用3P97非房室模型法生物等效性计算程序进行统计分析.结果:国产和进口奥氮平片单次口服后的血药浓度时间曲线相似,主要药动学参数Cmax分别为(20.77±4.86)和(19.31±4.80)μg·L-1;Tmax分别为(2.91±0.68)和(3.73±1.24)h;AUC0~144h分别为(643.94±156.35)和(636.53±187.19)μg·h·L1;AUC0~∞分别为(688.42±156.19)和(684.85±192.66)μg·h·L-1.国产奥氮平片对进口奥氮平片的相对生物利用度F-AUC0~144h为(105.2±25.0)%,F-AUC0~∞为(104.8±27.9)%.除Tmax外(P<0.05),主要药动学参数Cmax,AUC0~144h和AUC0~∞均无显著性差异(P>0.05).结论:国产和进口奥氮平片具有生物等效性.  相似文献   

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目的:比较国产与进口非那雄胺片的人体生物等效性.方法:18例健康男性单次随机交叉口服非那雄胺10mg后,用HPLC法测定血清中各时的药物浓度,计算两者的药物动力学参数和相对生物利用度,进行生物等效性评价.结果:国产及进口非那雄胺片的主要药动学参数如下:AUC0-t分别为(1039.13±272.37)和(1008.60±244.77)μg·h·L-1,Cmax分别为(128.72±26.69)和(117.32±25.20)μg·L-1,Tmax分别为(2.69±0.39)和(2.69±0.49)h,供试制剂相对于参比制剂的人体生物利用度为(106.58±27.79)%.结论:国产与进口非那雄胺片具有生物等效性.  相似文献   

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国产与进口盐酸特比萘芬在健康人体的生物等效性   总被引:1,自引:0,他引:1  
目的 比较国产与进口盐酸特比萘芬片(广谱抗真菌药)在健康人体的生物利用度和生物等效性.方法 20名健康受试者随机分组,双交叉单次口服国产(试验制剂)与进口(对照制剂)盐酸特比萘芬各250 mg,清洗期为1周.服药后于各时间点采血3 mL,用高效液相色谱法检测血药浓度,用DAS 2.0软件计算药代动力学参数,并进行生物等效性评价.结果 对照制剂和试验制剂的主要药代动力学参数:t1/2分别为(17.26±7.60),(17.94±7.94)h;AUC0-t分别为(5.20±2.06),(4.90±1.50)mg·h·L-1;AUC0-∞分别为(5.70±2.24),(5.40±1.74)mg·h·L-1;Cmax分别为(1.15±0.48),(1.03±0.36)mg·L-1;tmax分别为(1.56±0.74),(1.36±0.50)h.试验制剂的相对生物利用度F为104.4%.结论 国产和进口盐酸特比萘芬片生物等效.  相似文献   

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目的 比较巴罗沙星胶囊剂与片剂在健康人体内的生物等效性.方法 20名健康志愿者采用双周期交叉试验,单剂量空腹口服巴罗沙星胶囊和巴罗沙星片各200mg,HPLC法测定其血清中巴罗沙星浓度,血药浓度-时间数据经DAS2.0统计软件处理,计算主要药动学参数,并进行两种制剂的生物等效性评价.结果 巴罗沙星胶囊和巴罗沙星片的主要药动学参数分别为t1/2(5.666±1.085)和(7.020±2.658)h、cmax(2.912±0.848)和(2.637±0.780)μg/ml、tmax(1.238±0.631)和(1.400±0.615)h、AUC0-48(18.987±4.284)和(20.737±9.681)(μg·h)/ml.巴罗沙星胶囊的相对生物利用度为(105.30±43.47)%.结论 巴罗沙星片剂与胶囊剂具有生物等效性.  相似文献   

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目的:研究富马酸奎的平片的药动学及相对生物利用度.方法:受试者交叉口服单剂量(100mg)国产片与进口片,用高效液相色谱法测定血药浓度.结果:两种片剂的主要药动学参数:Tmax分别为(1.7±0.8)h与(1.6±0.7)h,Cmax分别为(100.4±18 9)μg·L-1与(100.0±17.8)μg·L-1,AUC0-t分别为(246.8±29.4)μg·L-1·h与(244.7±28.8)μg·L-1·h,AUC0-∞分别为(250.7±30.2)μg·L-1·h与(248.9±29.6)μg·L-1·h,T1/2分别为(1.8±0.5)h与(1.8±0.4)h,国产片相对于进口片的生物利用度为(101.9±7.4)%.结论:两种制剂具有生物等效性.  相似文献   

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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.
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.
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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.  相似文献   

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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.  相似文献   

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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.  相似文献   

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Advances in the molecular biological knowledge of neuronal nicotinic acetylcholine receptors (nAChRs) have led to a growing interest by the pharmaceutical industry in the development of novel compounds that selectively modulate nAChR function. The ability of (-)-nicotine, an activator of nAChRs, to enhance attentional aspects of cognition in animals and humans, to exert neuroprotective and anxiolytic-like effects, and presumably to mediate the negative correlation between smoking and Alzheimer's (and Parkinson's) Disease, has focused interest on the potential therapeutic utility of modulators of nAChR function for treatment of some of the deficits associated with these progressive, neurodegenerative conditions. Numerous compounds are known which activate nAChRs and which might serve as lead compounds toward the development of such agents. The pharmacologic diversity of neuronal nAChR subtypes suggests the possibility of developing selective compounds which would have more favourable side-effect profiles than existing agents. This broader class of agents, collectively called cholinergic channel modulators (ChCMs), is anticipated to encompass compounds which would have more favourable side-effect profiles than existing agents, which generally exhibit low selectivity. This selectivity may be achieved by preferentially activating some subtypes of nAChRs (i.e., Cholinergic Channel Activators, ChCAs) or inhibiting the function of other subtypes (Cholinergic Channel Inhibitors, ChCIs). An overview of the biology of nAChRs and the rationale for the use of ChCMs for the treatment of dementia related to neurodegenerative diseases are presented, followed by a discussion of lead compounds and compounds under consideration for clinical evaluation.  相似文献   

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