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