Niu Catherine Hui, Volesky Bohumil, Cleiman Daniel
Department of Chemical Engineering, University of Saskatchewan, 57 Campus Drive, Saskatoon, Saskatchewan, Canada S7N 5A9.
Water Res. 2007 Jun;41(11):2473-8. doi: 10.1016/j.watres.2007.03.013. Epub 2007 Apr 24.
Highly toxic arsenate occurs naturally in some well water as well as in industrial wastewaters. Removal of arsenate (As(V)) by biosorption with acid-washed crab shells (AWCS) is very sensitive to solution pH. It greatly increased when the solution pH was lowered from 3.44+/-0.07 to 2.51+/-0.02, but it was reduced at pH below 1.99+/-0.01. Change of solution pH not only affected the charged functional groups on AWCS but also the speciation of arsenate in solution. Increasing ionic strength of solution negatively affected the arsenic uptake. At ionic strength 0.1M, arsenic uptake was seriously depressed. Arsenic biosorption with AWCS was mainly through arsenate binding on the amide groups in the AWCS. AWCS has a dense structure and low extent of swelling in aqueous solutions. This might prevent effective arsenate access to the functional groups in AWCS.
剧毒的砷酸盐天然存在于一些井水中以及工业废水中。用酸洗蟹壳(AWCS)通过生物吸附去除砷酸盐(As(V))对溶液pH值非常敏感。当溶液pH值从3.44±0.07降至2.51±0.02时,去除率大幅增加,但在pH值低于1.99±0.01时则降低。溶液pH值的变化不仅影响AWCS上的带电官能团,还影响溶液中砷酸盐的形态。溶液离子强度的增加对砷的吸收产生负面影响。在离子强度为0.1M时,砷的吸收严重受到抑制。AWCS对砷的生物吸附主要是通过砷酸盐与AWCS中的酰胺基团结合。AWCS结构致密,在水溶液中的溶胀程度低。这可能会阻止砷酸盐有效地接触到AWCS中的官能团。