首页> 外文会议>Water quality technology conference and exposition (2005 WQTC conference proceedings) >BROMIDE REMOVAL IN SOURCE WATER BY ELECTROLYSIS – APROCESS FOR REDUCTION OF DBPs IN DRINKING WATER
【24h】

BROMIDE REMOVAL IN SOURCE WATER BY ELECTROLYSIS – APROCESS FOR REDUCTION OF DBPs IN DRINKING WATER

机译:电解去除源水中的溴-减少饮用水中DBP的过程

获取原文
获取原文并翻译 | 示例

摘要

Brominated THM specie is seventy five percent of the four regulated TTHM and hasrnsignificantly greater implications, especially DCBM, as drinking water contaminant thanrnchlorinated THM regarding human health. Of the four individual trihalomethanes, only highrnDCBM exposure was associated with spontaneous abortion both alone and after adjustment forrnthe other THMs [1]. This project explored the use of electrolysis with silver electrodes, coated Tirnelectrodes (DSA)* and combination of both to remove bromide from California SWP at PalmdalernWater District Treatment Plant, CA, USA. Herbert Henry Dow used electrolysis coupled with airrnstripping of brine that has high proportion of bromide to manufacture bromine [2]. In surfacernwater treatment, bromide occurs at very low levels and may form very low levels ofrnhypobromous acid (HOBr), hypobromic acid (HBr) and hypobromite (Obr-) ions duringrnelectrolysis especially if the energy provided is below the ionization energy for bromide. Thesernbyproducts are difficult to remove by air or gas stripping and make bromine available to formrnTTHM downstream. With silver electrodes at ambient temperature, silver ions released from thernanode immediately bond directly with all halogens to various degrees depending on theirrnconcentrations, current applied, contact time, and electrode spacing. Minimal amount of oxyhalidesrnare formed and power requirement is low. Varying current density and bromidernconcentration, positioning the electrolytic cell before coagulation and after sedimentation, andrnchanging electrode combinations (Silver/Silver, DSA/DSA, and Silver/DSA as cathode/anodernrespectively), bromide removal was achieved to varying degrees. This process in combinationrnwith enhanced coagulation can be used to substantially extend the life of biologically active GACrnfilter and ensure compliance with the USEPA Stage 2 DBPR, LRAA of 80μg/L TTHM.
机译:溴化THM物种占四种受管制TTHM的百分之七十五,对饮用水的污染比对人类健康的氯代THM具有更大的影响,尤其是DCBM。在四种单独的三卤甲烷中,只有高DCDC暴露与单独或调整其他THM后自然流产有关[1]。该项目探索了在美国加州PalmdalernWater地区处理厂利用银电极,镀膜Tirn电极(DSA)*以及两者的组合电解法从加利福尼亚SWP去除溴化物的方法。赫伯特·亨利·道(Herbert Henry Dow)将电解与空气中的溴化物比例高的卤水汽提相结合来生产溴[2]。在地表水处理中,特别是如果所提供的能量低于溴化物的电离能,则在电解过程中溴化物的含量非常低,并且可能形成非常低含量的次溴酸(HOBr),次溴酸(HBr)和次溴酸盐(Obr-)离子。这些副产物很难通过空气或气体汽提除去,并使溴可用于下游形成TTHM。在环境温度下使用银电极时,从其阳极释放的银离子会立即与所有卤素直接键合到不同程度,这取决于它们的浓度,施加的电流,接触时间和电极间距。生成的卤代氧化物数量最少,功率要求低。通过改变电流密度和溴化甲烷浓度,在凝结之前和沉淀之后放置电解池,并更换电极组合(分别使用银/银,DSA / DSA和银/ DSA作为阴极/阳极),可以实现不同程度的溴去除。该过程与增强的凝结作用相结合,可用于大幅延长具有生物活性的GACrnfilter的寿命,并确保符合USEPA Stage 2 DBPR,LRAA为80μg/ L TTHM的要求。

著录项

相似文献

  • 外文文献
  • 中文文献
  • 专利
获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号