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Book with abstracts from the COST Action 0905 meeting in ... - UMB

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THE IMMOBILISATION AND RETENTION OF SOLUBLE ARSENIC,<br />

CADMIUM AND ZINC BY BIOCHAR.<br />

L.Beesley 1 and M. Marmiroli. 2<br />

1 The James Hutton Institute, Craigiebuckler, Aberdeen. AB15 8QH, UK.<br />

2<br />

Department of Environmental Sciences, Section of Genetics and Biotechnologies, University<br />

of Parma, 43100 Parma, Italy.<br />

Keywords: biochar, cadmium, z<strong>in</strong>c, arsenic, heavy metals, sorption<br />

Water-soluble <strong>in</strong>organic pollutants may constitute an environmental toxicity problem if <strong>the</strong>ir<br />

movement through soils and potential transfer to plants or groundwater is not arrested. The<br />

capability of biochar to immobilise and reta<strong>in</strong> arsenic (As), cadmium (Cd) and z<strong>in</strong>c (Zn) <strong>from</strong><br />

a multi-element contam<strong>in</strong>ated sediment-derived soil was explored by a column leach<strong>in</strong>g<br />

experiment and scann<strong>in</strong>g electron microanalysis (SEM/EDX). Sorption of Cd and Zn to<br />

biochar’s surfaces assisted a 300 and 45 fold reduction <strong>in</strong> <strong>the</strong>ir leachate concentrations,<br />

respectively. Retention of both metals was not affected by considerable leach<strong>in</strong>g of watersoluble<br />

carbon <strong>from</strong> biochar, and could not be reversed follow<strong>in</strong>g subsequent leach<strong>in</strong>g of <strong>the</strong><br />

sorbant biochar <strong>with</strong> water at pH 5.5. Weakly water-soluble As was also reta<strong>in</strong>ed on biochar’s<br />

surface but leachate concentrations did not duly decl<strong>in</strong>e. It is concluded that biochar can<br />

rapidly reduce <strong>the</strong> mobility of selected contam<strong>in</strong>ants <strong>in</strong> this polluted soil system, <strong>with</strong><br />

especially encourag<strong>in</strong>g results for Cd.<br />

Introduction<br />

Biochar is a low-density charred material<br />

produced by burn<strong>in</strong>g biomass under<br />

conditions of low temperatures and m<strong>in</strong>imal<br />

oxygen. Experimental application of this<br />

material to soils to sequester carbon has been<br />

encouraged by its very high organic carbon<br />

content (Y<strong>in</strong> Chan et al., 2009). There are<br />

wider agro-environmental benefits of add<strong>in</strong>g<br />

biochar to soils, for example, <strong>in</strong>creas<strong>in</strong>g soil<br />

pH and reduc<strong>in</strong>g leach<strong>in</strong>g of soluble<br />

macronutrients (Novak et al., 2009).<br />

Application of biochar to real world<br />

contam<strong>in</strong>ated soil systems has received little<br />

systematic <strong>in</strong>vestigation to date but <strong>in</strong>itial<br />

trials are encourag<strong>in</strong>g regard<strong>in</strong>g <strong>the</strong> retention<br />

of both <strong>in</strong>organic and organic pollutants<br />

(Beesley et al., 2010). The present study<br />

evaluates <strong>the</strong> efficacy and permanence of<br />

As, Cd and Zn by biochar <strong>in</strong> a column<br />

leach<strong>in</strong>g test and by microanalysis<br />

(SEM/EDX).<br />

Materials and Methods<br />

Triplicate bulk soil samples were<br />

sourced <strong>from</strong> a canal embankment <strong>in</strong><br />

Kidsgrove, Staffordshire, UK, <strong>with</strong> a known<br />

history of heavy metals and As<br />

contam<strong>in</strong>ation (Beesley et al., 2010). Six<br />

glass leach<strong>in</strong>g columns (XK50, Pharmacia<br />

Biotech, UK), 20 cm <strong>in</strong> length and 5 cm <strong>in</strong><br />

<strong>in</strong>ternal diameter, were packed <strong>with</strong> 400g of<br />

air-dried soil (two columns) whilst <strong>the</strong><br />

rema<strong>in</strong><strong>in</strong>g four columns were packed to ¾ of<br />

<strong>the</strong>ir length <strong>with</strong> biochar (biochar had far<br />

lower density than soil).<br />

A. B.<br />

------- 300 µm ------- ------- 100 µm -------

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