研究报告

  • 童新,沃静静,孙明洋,汤婷媚,陆荣杰,徐新华.烟气脱硫液中共存离子对汞稳定化的影响[J].环境科学学报,2016,36(5):1602-1607

  • 烟气脱硫液中共存离子对汞稳定化的影响
  • Effects of co-existing ions on mercury stabilization in simulated flue gas desulfurization solutions
  • 基金项目:国家自然科学基金(No.21277119)
  • 作者
  • 单位
  • 童新
  • 1. 台州科技职业学院, 台州 318020;2. 浙江大学环境工程系, 杭州 310058
  • 沃静静
  • 浙江大学环境工程系, 杭州 310058
  • 孙明洋
  • 浙江大学环境工程系, 杭州 310058
  • 汤婷媚
  • 浙江大学环境工程系, 杭州 310058
  • 陆荣杰
  • 浙江大学环境工程系, 杭州 310058
  • 徐新华
  • 浙江大学环境工程系, 杭州 310058
  • 摘要:利用湿法烟气脱硫技术(Wet Flue Gas Desulfurization, WFGD)同步除汞被认为是最经济的燃煤烟气脱汞方式,但进入脱硫液的Hg2+易被还原并再次释放进入大气,造成二次污染.针对这一问题,本研究选择了常用的Na2S、三巯基均三嗪三钠盐(TMT)、二硫代氨基甲酸盐(DTC)等系列重捕剂,考察了投加量对Hg2+去除效果的影响,并筛选出了去除效果较好的3种类型重捕剂,探究了脱硫液中主要的阴阳离子(SO42-、NO3-、Ca2+、Mg2+)及重金属离子等共存离子对Hg2+去除效果的影响.结果表明:Na2S、TMT类重捕剂TMT-18和DTC类重捕剂DTCR-2的去除效果相对较好;SO42-、NO3-会抑制TMT-18和Na2S对Hg2+的去除,对DTCR-2稍有促进作用;Ca2+、Mg2+对TMT-18去除Hg2+有促进作用,而对Na2S有抑制作用;重金属离子会抑制重捕剂对Hg2+的去除效果,Cu2+和Pb2+对Hg2+螯合去除效果的影响较Ni2+和Zn2+要大,随着Cu2+和Pb2+浓度的增加,DTCR-2对Hg2+的去除显著降低,Cu2+浓度的影响尤为显著.本研究可为解决Hg2+在脱硫液中的还原再释放及二次污染问题,同时也为湿法烟气脱硫同时脱汞的工业应用提供理论依据.
  • Abstract:Wet flue gas desulfurization (WFGD) system used for sulfur dioxide (SO2) is proved to be effective for the co-removal of mercury (Hg) in coal-fired power plants. However, it may result in secondary atmospheric pollutions caused by the reduction of Hg2+ to Hg0. In this paper, Na2S, 2, 4, 6-trimercaptotiazine, trisodium salt nonahydrate (TMT-18) and sodium dithiocarbamate (DTC) were selected to precipitate aqueous Hg2+ in simulated desulfurization solutions. Moreover, the effects of co-existing ions (SO42-, NO3-, Ca2+, Mg2+ and heavy metal) on Hg2+ stabilization was investigated. DTCR-2, TMT-18, Na2S were found to be better in Hg2+ removal. The increment of SO42-、NO3- concentration inhibited Hg2+ precipitation by TMT-18 and Na2S, but it was beneficial for DTCR-2 to remove Hg2+. The Hg removal efficiency was increasing with the increment of Ca2+ and Mg2+ concentration except Na2S. The increment of heavy metals concentration inhibited Hg2+ precipitation efficiency to a considerable extent, especially Cu2+. Our results would provide theoretical basis for the co-removal of highly soluble oxidized Hg in the wet FGD systems.

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