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黏土絮凝沉降铜绿微囊藻的动力学及其作用机理
摘要点击 1755  全文点击 2396  投稿时间:2003-04-01  修订日期:2003-05-12
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中文关键词  铜绿微囊藻  黏土  水华  絮凝  机理  改性  架桥网捕  电中和
英文关键词  Microcystis aeruginosa  clays  algal blooms  flocculation  mechanism  clay modification  bridging and netting  electrostatic neutralization
作者单位
潘纲 中国科学院生态环境研究中心环境水质学国家重点实验室 北京100085 
张明明 中国科学院生态环境研究中心环境水质学国家重点实验室 北京100085 
闫海 中国科学院生态环境研究中心环境水质学国家重点实验室 北京100085 
邹华 中国科学院生态环境研究中心环境水质学国家重点实验室 北京100085 
陈灏 中国科学院生态环境研究中心环境水质学国家重点实验室 北京100085 
中文摘要
      研究了26种天然黏土矿物凝聚沉降铜绿微囊藻的动力学过程在投加量为0.7 g·L-1时按平衡除藻率和除藻速率将26种黏土分成3类.第1类矿物(滑石、三氧化二铁、海泡石、四氧化三铁、高岭土等)的8 h平衡除藻率大于90%,去除50%藻细胞所需时间t50<30 min,去除80%藻细胞所需时间t80<2.5 h第2类黏土(轻质页岩、陶土、凹凸棒、累托土、伊利土等7种)的8 h平衡除藻率为50%~80%,t50<2.5 h,t80>5 h.第3类黏土(铁矾土,云母,沸石、浮石、硅藻土、高钾长石和石英等14种)的8 h平衡除藻率低于50%,t50>>8 h.当投加量逐步降低到0.2~0.1 g·L-1时,25种黏土矿物的8 h平衡除藻率均降到60%以下,只有第1类黏土中的海泡石仍接近90%.与黏土相比,在0.02~0.2 g·L-1投加量下单独使用聚合氯化铝(PAC)时的8 h平衡除藻率均低于40%.进一步对海泡石进行电性改性后发现,虽然黏土颗粒表面电位的提高(pH 7.4时,Zeta电位由-24.0 mV提高到+0.43 mV)可以显著加快海泡石的除藻速率,但其平衡除藻率并没有显著提高.在分析了本研究中的凝聚机理后提出:架桥网捕作用可能在黏土-藻凝聚过程中发挥了十分关键的作用,增强黏土对藻细胞的架桥网捕作用可能是今后进一步提高除藻效率、大幅度降低投加量的一个重要方向.
英文摘要
      Twenty-six natural clays were studied for their kinetics of flocculating and removing algal cells of Microcystis aeruginosa. According to the 8 h equilibrium removal efficiencies and removal rates at a clay-loading of 0.7 g·L-1, all the 26 clays were classified into three categories. Type-I clay, which includes talc, ferric oxide, sepiolite, ferroferric oxide, and kaolinite, has an equilibrium removal efficiency greater than 90%, a t50 (time needed to remove 50% of the algae) of less than 30 min, and a t80 (time needed to remove 80% of the algae) of less than 2.5 h. Type-Ⅱ clay, which includes argillanceous rocks, attapulgite, rectorite, illite, and argil, etc., has an equilibrium removal efficiency of 50%~80%, a t50 of less than 2.5 h, and a t80 of more than 5 h. Type-Ⅲ clay consists of 14 minerals, including laterite, zeolite, mica, clinoptilolite, pumice, tripoli, feldspar and quartz, etc. with the removal efficiency less than 50%, and t50 8h. When the clay loading was decreased to 0.1~0.2 g·L-1, the 8 h equilibrium removal efficiencies for 25 clays declined to below 60%, except for sepiolite, a Type-I clay, which maintained around 90%. After the sepiolite was modified with Fe3+ to increase its surface charge (Zeta potential from -24.0 mV to +0.43 mV at pH 7.4), the initial removal rate was increased remarkably although its 8 h equilibrium removal efficiency was not improved substantially. As a comparison, the 8 h equilibrium removal efficiency of PAC was no greater than 40% at loadings of 0.02~0.2 g·L-1. Following the analysis of the flocculation mechanism it was concluded that the effect of bridging and netting may play a key role in the clay-algae flocculation processes, which may be important for selecting and modifying clays to improve significantly the removal efficiency.

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