有色金属科学与工程
有色金屬科學與工程
유색금속과학여공정
JIANGXI NONFERROUS METALS
2014年
4期
66-70
,共5页
唐敏康%陈苹%许建红%高乃云%肖爱红
唐敏康%陳蘋%許建紅%高迺雲%肖愛紅
당민강%진평%허건홍%고내운%초애홍
Fe(Ⅱ)-H2O2%吸附%砷%铁效率%纳米羟基铁
Fe(Ⅱ)-H2O2%吸附%砷%鐵效率%納米羥基鐵
Fe(Ⅱ)-H2O2%흡부%신%철효솔%납미간기철
Fe(Ⅱ)-H2O2%adsorption%arsenate%iron use efficiency%nano-iron hydroxides
Fe(Ⅱ)-H2O2不同温度浸润改性活性炭是采用FeSO4·7H2O添加H2O2在温度100℃下纯浸润24 h(Fe(Ⅱ)-24 h)和高温蒸发15 min(Fe(Ⅱ)-15 min)制备.对2类材料进行SEM表征并对其吸附1.1 mg/L砷(V)的性能进行比较.SEM显示Fe(Ⅱ)(0.485%)-24 h(0.485%为Fe(Ⅱ)-24 h的铁含量,下同)表面覆盖厚的棒状纳米羟基铁,Fe(Ⅱ)(1.35%)-15 min表面覆盖薄而烧结扭曲羟基铁;高温蒸发15 min有利于铁负载;Fe(Ⅱ)-24 h(108~142 mg/gFe)对砷(V)吸附的铁效率是Fe(Ⅱ)-15 min(57~63 mg/gFe)的2倍;Fe(Ⅱ)(0.485%)-24 h在2<pH<3.5或9<pH<12时对砷(V)的吸附平衡容量高于Fe(Ⅱ)(1.35%)-15 min,同时Fe(Ⅱ)(0.485%)-24 h在不同pH值的条件下铁的溶出量低于Fe(Ⅱ)(1.35%)-15 min;SO42-、NO3-、ClO4-、PO43-抑制Fe(Ⅱ)(0.485%)-24 h对砷(V)的去除,PO43-抑制效果更为明显,Cl-(100 mg/L)和BrO3-促进其对砷(V)的去除.
Fe(Ⅱ)-H2O2不同溫度浸潤改性活性炭是採用FeSO4·7H2O添加H2O2在溫度100℃下純浸潤24 h(Fe(Ⅱ)-24 h)和高溫蒸髮15 min(Fe(Ⅱ)-15 min)製備.對2類材料進行SEM錶徵併對其吸附1.1 mg/L砷(V)的性能進行比較.SEM顯示Fe(Ⅱ)(0.485%)-24 h(0.485%為Fe(Ⅱ)-24 h的鐵含量,下同)錶麵覆蓋厚的棒狀納米羥基鐵,Fe(Ⅱ)(1.35%)-15 min錶麵覆蓋薄而燒結扭麯羥基鐵;高溫蒸髮15 min有利于鐵負載;Fe(Ⅱ)-24 h(108~142 mg/gFe)對砷(V)吸附的鐵效率是Fe(Ⅱ)-15 min(57~63 mg/gFe)的2倍;Fe(Ⅱ)(0.485%)-24 h在2<pH<3.5或9<pH<12時對砷(V)的吸附平衡容量高于Fe(Ⅱ)(1.35%)-15 min,同時Fe(Ⅱ)(0.485%)-24 h在不同pH值的條件下鐵的溶齣量低于Fe(Ⅱ)(1.35%)-15 min;SO42-、NO3-、ClO4-、PO43-抑製Fe(Ⅱ)(0.485%)-24 h對砷(V)的去除,PO43-抑製效果更為明顯,Cl-(100 mg/L)和BrO3-促進其對砷(V)的去除.
Fe(Ⅱ)-H2O2불동온도침윤개성활성탄시채용FeSO4·7H2O첨가H2O2재온도100℃하순침윤24 h(Fe(Ⅱ)-24 h)화고온증발15 min(Fe(Ⅱ)-15 min)제비.대2류재료진행SEM표정병대기흡부1.1 mg/L신(V)적성능진행비교.SEM현시Fe(Ⅱ)(0.485%)-24 h(0.485%위Fe(Ⅱ)-24 h적철함량,하동)표면복개후적봉상납미간기철,Fe(Ⅱ)(1.35%)-15 min표면복개박이소결뉴곡간기철;고온증발15 min유리우철부재;Fe(Ⅱ)-24 h(108~142 mg/gFe)대신(V)흡부적철효솔시Fe(Ⅱ)-15 min(57~63 mg/gFe)적2배;Fe(Ⅱ)(0.485%)-24 h재2<pH<3.5혹9<pH<12시대신(V)적흡부평형용량고우Fe(Ⅱ)(1.35%)-15 min,동시Fe(Ⅱ)(0.485%)-24 h재불동pH치적조건하철적용출량저우Fe(Ⅱ)(1.35%)-15 min;SO42-、NO3-、ClO4-、PO43-억제Fe(Ⅱ)(0.485%)-24 h대신(V)적거제,PO43-억제효과경위명현,Cl-(100 mg/L)화BrO3-촉진기대신(V)적거제.
Granular activated carbon (GAC) modified by Fe(Ⅱ)-H2O2 incipient wetness impregnation at different temperatures are prepared by FeSO4·7H2O and hydrogen peroxide (H2O2) via the incipient wetness for 24 h at 100℃(Fe(Ⅱ)-24 h ) and the high temperature evaporation for 15 min (Fe(Ⅱ)-15 min).Fe(Ⅱ)-24 h and Fe(Ⅱ)-15 min are characterized by SEM and are compared for the adsorption behavior of the arsenate (1.1 mg/L).The SEM has shown that nano-iron hydroxides are formed on the surface of Fe (Ⅱ)(0.485 %)-24 h (0.485 % is the iron content of Fe (Ⅱ)-24 h,the same below) and that sintering distorted hydroxides are formed on the surface of Fe (Ⅱ)(1.35 %)-15 min.The high temperature evaporation for 15 min is favorable for iron to load on GAC. The iron use efficiency of Fe(Ⅱ)-24 h(108~142 mg/gFe) is two fold of that of Fe(Ⅱ)-15 min(57~63 mg/gFe).The arsenate equilibrium adsorption capacity of Fe(Ⅱ) (0.485 %)-24 h is better than the Fe(Ⅱ)(1.35 %)-15 min at pH 2~3.5 or 9~12,at the same time,the soluble iron at any particular pH released from the Fe(Ⅱ)(0.485 %)-24 h is less than that released from the Fe (Ⅱ)(1.35 %)-15 min.The presence of SO42-, NO3-, ClO4-, or PO43-inhibit the adsorption of arsenate, especially for phosphate,while the existence of Cl-(100 mg/L)and BrO3-promote the adsorption of arsenate.