UK fly ash-based zeolites as adsorbents for removal of heavy metals and ammonium from artificially polluted solutions
被引:0
作者:
Rios, Carlos A.
论文数: 0引用数: 0
h-index: 0
机构:
Univ Ind Santander, Escuela Geol, Bucaramanga, ColombiaUniv Ind Santander, Escuela Geol, Bucaramanga, Colombia
Rios, Carlos A.
[1
]
Williams, Craig D.
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h-index: 0
机构:
Univ Wolverhampton, Sch Appl Sci, Wolverhampton, EnglandUniv Ind Santander, Escuela Geol, Bucaramanga, Colombia
Williams, Craig D.
[2
]
Roberts, Clive L.
论文数: 0引用数: 0
h-index: 0
机构:
Univ Wolverhampton, Sch Appl Sci, Wolverhampton, EnglandUniv Ind Santander, Escuela Geol, Bucaramanga, Colombia
Roberts, Clive L.
[2
]
机构:
[1] Univ Ind Santander, Escuela Geol, Bucaramanga, Colombia
[2] Univ Wolverhampton, Sch Appl Sci, Wolverhampton, England
来源:
INGENIERIA Y COMPETITIVIDAD
|
2010年
/
12卷
/
01期
关键词:
Fly ash;
Zeolite synthesis;
Heavy metal;
Ammonium;
Uptake;
D O I:
暂无
中图分类号:
T [工业技术];
学科分类号:
08 ;
摘要:
Fly ash (FA) from the Rugeley Power Station, West Midlands (England) was used in this study as starting material in zeolite synthesis at laboratory scale using NaOH and KOH solutions. Na-phillipsitc, hydroxysodalite and K-chabazite were synthetized from FA using the classic hydrothermal route. The FA-based zeolites (FAZs) were employed as heavy metal and ammonium adsorbents from aqueous solutions artificially polluted with selected metals and other contaminants. Finally, with the aim of testing possible applications of the FAZs in water decontamination, efficiency for heavy metal and ammonium uptake from synthetic solutions using batch reactions at room temperature was investigated. Important parameters such as zeolite dose (g) per effluent volume unit (ml) and reaction time were examined in order to understand the removal mechanisms involved. The efficiency of the FAZs shows that these FAZs may reach CECs appropriate for their application in industrial wastewater treatment. The heavy metal selectivity of Na-phillipsite was determined as Cu>Zn>Cr>Ni>Pb, and it also showed a high affinity for NH4+.