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2017


               qiangWang.

                    WATER RESEARCH  卷 : 109   页 : 337-346   出版年 : FEB 1 2017
                    摘  要:Severe health problems due to elevated arsenic (As) in groundwater have made it

               urgent to develop cost-effective technologies for As removal. This field experimental study tested
               the feasibility of in-situ As immobilization via As incorporation into newly formed biogenic

               Fe(II) sulfides in a typical As-affected strongly reducing aquifer at the central part of Datong
               Basin, China. After periodic supply of FeSO4 into the aquifer for 25 d to stimulate microbial

               sulfate reduction, dissolved sulfide concentrations increased during the experiment, but the
               supplied Fe(II) reacted quickly with sulfide to form Fe(II)-sulfides existing majorly as mackinawite

               as well as a small amount of pyrite-like minerals in sediments, thereby restricting sulfide build-
               up in groundwater. After the completion of field experiment, groundwater As concentration

               decreased from an initial average value of 593 μg/L to 159 μg/L, with an overall As removal
               rate of 73%, and it further declined to 136 μg/L adding the removal rate up to 77% in 30 d after

               the experiment. The arsenite/Astotal ratio gradually increased over time, making arsenite to be
               the predominant species in groundwater residual As. The good correlations between dissolved

               Fe(II), sulfide and As concentrations, the increased abundance of As in newly-formed Fe sulfides
               as well as the reactive-transport modeling results all indicate that As could have been adsorbed

               onto and co-precipitated with Fe(II)-sulfide coatings once microbial sulfate reduction was
               stimulated after FeSO4 supply. Under

               the strongly reducing conditions, sulfide
               may facilitate arsenate reduction into

               arsenite and promote As incorporation
               into pyrite or arsenopyrite. Therefore,

               the major mechanisms for the in-situ As-
               contaminated groundwater remediation

               can be As surface-adsorption on and co-
               precipitation with Fe(II) sulfides produced

               during the experimental period.
                    论文链接:https://doi.org/10.1016/j.watres.2016.10.056

                    3.Intrawellbore kinematic and frictional losses in a horizontal well in a bounded

               confined aquifer
                    作  者 : Wang Quanrong; Zhan,Hongbin*.


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