Earthworms as agents for arsenic transport and transformation in
roxarsone-impacted soil mesocosms: A μXANES and modeling study
A.K. Covey
a
, D.J. Furbish
a
, K.S. Savage
a,b,
⁎
a
Earth and Environmental Sciences, Vanderbilt University, Nashville, TN, USA
b
Environmental Studies, Wofford College, Spartanburg, SC, USA
abstract article info
Article history:
Received 26 June 2009
Received in revised form 17 January 2010
Accepted 6 February 2010
Available online 11 March 2010
Keywords:
Oligochaetia
Soil management
Contaminant transport
Borings
XANES spectra
Mathematical models
Earthworms influence soil mixing during their feeding and burrowing activities by causing physical
displacement and chemical transformations, potentially impacting the distribution and speciation of soil
contaminants. This study investigates the effects of burrowing earthworms on arsenic speciation and
mobility in soil mesocosms treated with roxarsone, an increasing anthropogenic source of arsenic used in the
poultry industry as a feed supplement. Experiments were designed to test the hypothesis that earthworms
and burrows provide means for biotransformation and redistribution of arsenic. Arsenic distribution was
determined following earthworm bioturbation in artificial soil columns that were initially constructed with a
contaminated layer of designated thickness and depth. The resulting depth profiles were used to indicate
bioturbation rates by fitting them to a simple one-dimensional advection/diffusion model with a
biodiffusivity that decreases with depth. Synchrotron X-ray methods reveal additional small-scale
displacement of arsenic near the burrow and in the bulk soil. Microbeam X-ray Absorption Near Edge
Structure spectra were collected to determine arsenic speciation. Arsenic initially introduced as roxarsone
tended to be in a methylated form after 30 days. Within the earthworm tissue, arsenic–glutathione
complexes were formed. Results are viewed in the context of poultry litter used as agricultural fertilizer. A
decrease in tillage arising from soil conservation efforts allows earthworm populations to increase and
burrows to become more permanent. This study suggests that (1) burrows serve as macropores allowing
rapid transport of arsenic to greater depths during infiltration events; (2) bioturbation rates appear to be
depth-dependent; and (3) earthworm soil mixing produces potentially mobile forms of arsenic that may
become bioaccessible as arsenic is transported through the subsurface.
© 2010 Elsevier B.V. All rights reserved.
1. Introduction
Since 2001, when the United States Environmental Protection
Agency (EPA) passed stricter regulations on arsenic in drinking water,
reducing allowable concentrations from 50 to 10 μg/L, increasing
attention has been given to the agricultural feeding practices of
poultry and swine. In particular, 3-nitro 4-hydroxphenylarsonic acid
or roxarsone (ROX) is used as a supplemental additive in poultry feed.
ROX is an organoarsenic compound first introduced to feed in the
1940s in order to increase weight gain, feeding efficiency (ratio of feed
eaten to slaughter weight), and to control pigmentation and coccidial
intestinal parasites (Han et al., 2004; Nachman et al., 2005; Cortinas
et al., 2006; Jackson et al., 2006; Nachman et al., 2008). With more
attention on arsenic poisoning, concern has been growing over the
levels contained in tissue and meat (Lasky et al., 2004; Wallinga,
2006), although the majority of arsenic is excreted into the litter
(Morrison, 1969).
1.1. Arsenic in poultry litter
According to the Poultry—Production and Value 2007 Summary
Report (NASS, National Agricultural Statistics Service, 2008) there
were 8.9 billion broilers produced in the U.S (∼ 7% increase since
1996). If the average bird produces up to 4.9 kg of waste in its 48-day
lifetime (ASAE, American Society of Agricultural Engineers, 2005) the
annual production would be 44 billion kilograms of waste. Garbarino
et al. (2003) estimate that 70% of broilers are treated with ROX and
each excretes 150 mg of ROX. Based on the 2007 production census,
this is expected to result in 9.3 × 10
5
kg of ROX or 2.7 × 10
5
kg As. With
an increase in poultry production, along with decreasing numbers of
farms, the problems associated with disposal of litter waste in
concentrated areas are growing. The current practice is land
application for fertilizer, while other uses are slowly coming online,
such as biomass-fueled power plants and pelletization (Nachman
et al., 2008).
Geoderma 156 (2010) 99–111
⁎ Corresponding author. Present address: Environmental Studies, Wofford College,
Spartanburg, SC, USA.
E-mail address: savageks@wofford.edu (K.S. Savage).
0016-7061/$ – see front matter © 2010 Elsevier B.V. All rights reserved.
doi:10.1016/j.geoderma.2010.02.004
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