Environmental and Experimental Botany 69 (2010) 24–31
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Environmental and Experimental Botany
journal homepage: www.elsevier.com/locate/envexpbot
Mapping of nickel in root cross-sections of the hyperaccumulator plant Berkheya
coddii using laser ablation ICP-MS
Ahmad B. Moradi
a,∗
, Siegfried Swoboda
b
, Brett Robinson
a
, Thomas Prohaska
b
, Anders Kaestner
c
,
Sascha E. Oswald
d
, Walter W. Wenzel
e
, Rainer Schulin
a
a
Soil Protection group, Institute of Terrestrial Ecosystems, Dept. of Environmental Science, ETH Zürich, Switzerland
b
Dept. of Chemistry, University Natural Resources & Applied Life Science, Vienna, Austria
c
Paul Scherrer Institute, Villigen, Switzerland
d
Helmholtz Centre for Environmental Research -UFZ, Leipzig, Germany
e
Dept. of Forest & Soil Science, University Natural Resources & Applied Life Science, Vienna, Austria
article info
Article history:
Received 7 August 2009
Received in revised form 19 January 2010
Accepted 4 February 2010
Keywords:
Berkheya coddii
Cortex
Dimethylglyoxime
Laser ablation
Nickel
Root cross-section
Stele
abstract
Quantitative studies of the distribution pattern of metals in plant tissues provide important information
on the potential of metal-accumulator plants for remediation and amelioration of contaminated soils. We
used laser ablation inductively coupled plasma mass spectrometry (LA-ICP-MS) as well as staining with
dimethylglyoxime (DMG) to investigate the distribution pattern of nickel (Ni) in root cross-sections of the
Ni-hyperaccumulator plant Berkheya coddii Rossler. Plants were grown in rhizoboxes containing soil with
125 mg kg
−1
Ni. Roots were embedded in resin and cut into sections for LA-ICP-MS analysis. For DMG-
staining analysis, fresh root cross-sections were prepared using a microtome. LA-ICP-MS revealed higher
Ni concentrations in the cortex (374 ± 66 mg kg
−1
) than in the stele (210 ± 48 mg kg
−1
) of the investigated
roots. The distribution pattern agreed well with those found by DMG-staining. Higher concentrations of
Ni were found in the stele compared to the cortex of roots of the control plants not exposed to elevated
soil Ni using both techniques. Our results indicate that an active uptake or ion selection mechanism exists
for B. coddii in the absence of available Ni in the rhizosphere.
© 2010 Elsevier B.V. All rights reserved.
1. Introduction
Hyperaccumulator plants may offer a sustainable treatment
option for the remediation of metal-contaminated sites (mining
activity, refinery emissions, waste disposal, fossil fuel combustion,
and agricultural application of pesticides and biosolids) and also
an opportunity to mine naturally metal-rich soils i.e., phytomin-
ing of ultramafic soils (Brooks et al., 1998; Angle et al., 2001; Li et
al., 2003). Berkheya coddii Rossler is a Ni-hyperaccumulator plant
that has attracted particular attention because of its high Ni con-
centration and rapid biomass production. Robinson et al. (1997)
reported an annual biomass production of 22 t ha
−1
and up to 1%
(w:w) Ni in the above-ground biomass. The combination of these
two traits is rare and makes this plant suitable for the remedia-
tion of Ni-contaminated soils by means of phytoextraction. Even
Abbreviations: LA-ICP-MS, laser ablation combined with inductively coupled
plasma mass spectrometry; DMG, dimethylglyoxime; ICP-OES, inductively coupled
plasma optical emission spectrometry; XRF, X-ray fluorescence.
∗
Corresponding author. Present address: Hydrogeology Department, Helmholtz
Centre for Environmental Research - UFZ, Permoserstraße 15, 04318 Leipzig,
Germany. Tel.: +49 341 235 1982; fax: +49 341 235 451985.
E-mail address: ahmad.moradi@ufz.de (A.B. Moradi).
though some aspects of metal uptake by hyperaccumulator plants
are already known (Kramer et al., 1996; Hall, 2002), these mecha-
nisms might be different among different plants. Unravelling these
mechanisms and interactions is necessary in order to improve phy-
toextraction and phytomining techniques of Ni from contaminated
and naturally-rich soils (McNear et al., 2005).
The highest Ni concentration occurs in the shoots of hyperac-
cumulators. Therefore, shoots and particularly leaf tissue has been
the subject of previous investigations (Robinson et al., 2003; Bhatia
et al., 2004; Budka et al., 2005; Berazain et al., 2007; de la Fuente
et al., 2007; Tappero et al., 2007; Moradi et al., 2009). Proton or
nuclear microprobe analyses of B. coddii collected from native South
African ultramafic soils showed that Ni was concentrated in the
mesophyll and epidermis of the leaves (Mesjasz-Przybylowicz et
al., 2001). Although roots are the prime site of uptake of metals, the
distribution of Ni in root tissues of B. coddii has rarely been investi-
gated. Most research regarding Ni hyperaccumulation and uptake
has been carried out on Ni hyperaccumulator plants of the fam-
ily Brassicaceae and it is unclear whether other hyperaccumulators
have the same uptake mechanism and distribution pattern as the
Brassicaceae family (Robinson et al., 2003).
Methods currently used for spatial localisation of metals within
biological tissues are primarily micro analytical techniques based
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doi:10.1016/j.envexpbot.2010.02.001