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<strong>The</strong> 5th Cross-strait Conference on Structural and Geotechnical Engineering (SGE-5)<br />

<strong>Hong</strong> <strong>Kong</strong>, China, 13-15 July 2011<br />

ADSORPTION AND DESORPTION BEHAVIOR OF BIVALENT NICKEL AND<br />

MANGANESE IONS ON LOESS SOIL<br />

Y. Wang 1 , X. W. Tang 1, * , H. Y. Wang 1 and Z. F. Sun 1<br />

1<br />

MOE Key Laboratory of Soft Soils and Geoenvironmental Engineering, Zhejiang <strong>University</strong>, China.<br />

* Corresponding author. Email: tangxiaowu@zju.edu.cn<br />

ABSTRACT<br />

Both nickel and manganese are trace heavy metals. Toxic effect will be caused by excessive intake of these<br />

heavy metals. <strong>The</strong> control of heavy metal discharge into environment has been paid much attention recently.<br />

Loess soil was used to study the behavior of removing Ni(II) and Mn(II) from aqueous solutions. <strong>The</strong> kinetic<br />

data fit the pseudo-second order kinetics model very well, and the adsorption rate of Mn(II) was faster than that<br />

of Ni(II). <strong>The</strong> adsorption capacity of loess soil for Ni(II) and Mn(II) was determined to be 13.84 and 7.65 mg g -1<br />

respectively. <strong>The</strong> D-R model fit the isothermal data of Ni(II) and Mn(II) adsorption on loess soil best, and the<br />

main adsorption mechanism was ion exchange for both the heavy metals. NTA had contribution to desorption of<br />

heavy metals from loess soil. <strong>The</strong> maximum desorption ratio of Ni(II) and Mn(II) from loess soil was 63 % and<br />

92% respectively, and heavy metal ions could be more easily desorbed from the loess soil loaded with less<br />

heavy metal. <strong>The</strong>se results have significant reference value for loess soil as a material removing heavy metals<br />

and recycling use of heavy metal contaminated loess.<br />

KEYWORDS<br />

Loess soil, nickel, manganese, adsorption, desorption.<br />

INTRODUCTION<br />

1. Heavy metal contamination in environments has aroused a lot of public attention around the world.<br />

Accumulation of excessive amounts of trace elements (such as nickel and manganese) in soils and waters<br />

can result in severe toxic effects to human and ecosystems. Nickel and manganese can be released into<br />

environments by many different ways such as mine smelting, industrial waste disposal, electroplating and<br />

battery manufacturing processes (Kadirvelu et al. 2008). Heavy metal ions can easily be bioaccumulated and<br />

spread along the food chain once entering soil or water. <strong>The</strong> level of heavy metals in environments needs<br />

limiting to allowable value.<br />

2.<br />

Many researchers show interest in working on the technology of removing heavy metals from environment, and<br />

adsorption method is popular due to its effectiveness and convenience. Chinese loess soil with abundant clay<br />

minerals may be a potential promising material for removing heavy metals. Removal of Cu(II), Zn(II), Pb(II)<br />

and Cd(II) from aqueous solutions using Chinese loess have recently been reported and the loess shows high<br />

affinities for heavy metals (Tang et al. 2008ab; Li et al. 2009; Wang et al. 2009). In this study, adsorption<br />

behavior of loess soil towards Ni(II) and Mn(II) was investigated. In order to recycle the loess soil contaminated<br />

by heavy metals, NTA (nitrilotriacetic acid) which is environmental-friendly was used to desorb heavy metals<br />

from loess soil.<br />

MATERIALS AND METHODS<br />

Preparation of Materials<br />

Chinese loess soil samples were taken from the suburban area of Xi’an, located in northwestern China. <strong>The</strong><br />

loess soil was typical Quaternary loess on the Chinese Loess Plateau. <strong>The</strong> air-dried loess soil was oven-dried at<br />

105 o C for 24 h for removing bulk water, cooled to room temperature, and then sealed in plastic bags for storage.<br />

<strong>The</strong> basic parameters and chemical compositions of loess are summarized in Table 1 and 2. <strong>The</strong> reagent nickel<br />

chloride hexahydrate (NiCl 2·6H 2 O) and manganese chloride tetrahydrate (MnCl 2·4H 2 O) used in this study were<br />

of analytical grade. Ni(II) and Mn(II) stock solution (1 g L -1 ) was separately prepared in deionized water (DW).<br />

Erlenmeyer flasks and centrifuge tubes were pre-treated, immersed in 0.01 M HNO 3 solution for 24 h firstly, and<br />

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