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Development of Electrodialysis system for inactivation viruses in water.

Development of Electrodialysis system for inactivation viruses in water.
开发灭活水中病毒的电渗析系统。
批准号:
08680608
负责人:
SATO Toshio
金额:
$1.47万
依托单位:
依托单位国家:
日本
项目类别:
Grant-in-Aid for Scientific Research (C)
财政年份:
1996
资助国家:
日本
项目状态:
已结题
起止时间:
1996 至 1997

项目摘要

项目成果

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中文摘要
翻译
现行工作小说方法的目的是消除微生物对氯耐药性微生物已被禁止产生影响。由于氯离子产生的钙离子是这样的,氯离子的注射量应该减少为低的可能性。更远的地方,我们发现了一种电子病毒对氯的抵抗力比共聚物更强。我们已经确认,具有离子交换膜的电分解系统具有细菌效应。这一过程可能对电子病毒产生影响。本研究计划在聚合物Qbeta上应用树脂封装的电化学系统,其中将人类电子病毒在大小、形态学、结构和组成中的大小、形态学、结构和组成中的非激活指示器,似乎将病毒作为统计的高于6个室的使用的电化学装置。Cation-和Anion-交换的成员被设置为每个房间的解释。一对碳板是你的 ... More sed是electrodes和set of electrolysis apparatus的两个方面。治疗室用各种形式的离子交换树脂包装,如OH^-或Cl^-形式的离子交换树脂, H^+或Na^+形式的离子交换树脂。5个没有治疗室填充了NaCl溶液的室。Qbeta挂起的deionized water (10^8 PFU-ml^<-1>)从较低的治疗室通过到较高的花速率为3cm^3·min^<-1>,并通过了各种电流密度的电解。Qbeta的存活片段(N_t/N_0)和测量的有效pH值.结果和讨论[A]中Qbeta的失活||A-OH ; anion-exchange membrane| OH-表格anion-交换树脂|anion-交换膜]和[A]|| A-Cl]由于增加了当前的密度而变得更有效。电分析系统(C)||[C]和[C]|| C-Na]与[A]相比没有效果的对比||A] systems。这可能会导致Qbeta在[A]的电分析系统中的不激活||A:Qbeta是由阴离子交换沉积物的吸收效应增强的。在最有效的系统中,A|| A-OH,Qbeta在37.5 mA的当前密度下完全被杀死,开始电分析的不激活Qbeta将被当前集中的OH^-或H^+的加速进一步在该区域表面的邻近地区,自从在该区域表面上对Qbeta的吸收和当前流动在治疗室是Qbeta的两个主要因素。Less(低)
英文摘要
Purpose of present workNovel method to disinfect the microorganisms which have effective on chlorine resistant microorganisms have been anticipated. Since chlorination produce carcinogens such as trihalomethane, the injection volume of chlorine should be reduced as low as possible. Furthermore, it was found that enteric viruses were more resistant to chlorination than coliform. We were confirmed that electrodialysis system with ion-exchange membranes have bactericidal effect. Such procedure may be effective on enteric viruses.This study was planned to apply a resin packed electrodialysis sytem on the inactivation of coliphage Qbeta, which resembles to human enteric viruses in size, morphology, structure and composition, seems to be anadequate indicator for inactivation of the viruses as stated above.Material and MethodThe used electrodialysis apparatus consisted of 6 chambers. Cation- and anion-exchange membranes were set as the diaphragms of each chamber. A pair of carbon plates was u … More sed as electrodes and set both side of electrolysis apparatus. The treatment chamber was packed with various form ion-exchange resins, such as the OH^- or Cl^- form anion-exchange resin, H^+ or Na^+ form cation-exchange resin. 5 chambers without a treatment chamber were filled up NaCl solution.Qbeta suspended deionized water (10^8 PFU-ml^<-1>) were passed through the treatment chamber from lower to upper at a floe rate of 3cm^3・min^<-1>, and electrodialysis carried out various current densities. The surviving fraction (N_t/N_0) of Qbeta and the pH value of the effluent were measured.Result and DiscussionThe inactivation of Qbeta in the electrodialysis system of [A||A-OH ; anion-exchange membrane | OH-form anion-exchange resin | anion-exchange membrane] and [A||A-Cl] became more effective with increasing the current density. The electrodialysis system of [C||C-H] and [C||C-Na] were less effective contrary to that of [A||A] systems. It could be presumed that the inactivation of Qbeta with the electrodialysis systems of [A||A] was enhanced by the Qbeta adsorptive effect of the anion-exchange resins. In the most effective system as A||A-OH,Qbeta were complete killed at current densities of 37.5 mA after beginning of the electrodialysisThe inactivation Qbeta would be further accelerated by the current of the concentrated OH^- or H^+ in the neighborhood of the surface of the resins, since the adsorption of Qbeta on the resin surface and the current flowed in the treatment chamber were two main factors for the inactivation of Qbeta. Less
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