Environmental and Experimental Botany 78 (2012) 1–9
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Environmental and Experimental Botany
journa l h omepa g e: www.elsevier.com/locate/envexpbot
The early response of Arabidopsis thaliana to cadmium- and copper-induced
stress
Ana Martínez-Pe ˜ nalver, Elisa Gra ˜ na, Manuel J. Reigosa, Adela M. Sánchez-Moreiras
∗
Dept of Plant Biology and Soil Science. Faculty of Biology. University of Vigo, Campus Lagoas-Marcosende s/n, 36310 Vigo, Spain
a r t i c l e i n f o
Article history:
Received 13 January 2011
Received in revised form
12 December 2011
Accepted 14 December 2011
Keywords:
Heavy metals
Abiotic stress
Chlorophyll a fluorescence
Photosynthesis
Early symptoms
Hydrogen peroxide
a b s t r a c t
To investigate the early (first day) effects of cadmium and copper poisoning, adult plants of thale cress
(Arabidopsis thaliana L.) were treated with nutrient solution containing 50–100 M Cd
2+
or Cu
2+
. The
main effect of Cu
2+
treatment was a temporary reduction in F
v
/F
m
with respect to controls, which is
suggestive of transient damage to the antenna. By contrast, within 3 h of Cd
2+
treatment, leaf chlorophyll
and carotenoid contents and photochemical operating efficiency (ϕ
II
) fell with respect to controls, while
q
N
and ETR rose and F
v
/F
m
remained essentially unaltered. Protein content fell initially and rose within
24 h, and a transient widespread increase in H
2
O
2
production around hour 6 evolved by hour 24 to more
intense production around leaf veins when plants were watered with Cd
2+
. These alterations were not
due to induced nutrient deficiency, and are interpreted as suggestive of damage to the biochemical phase
of photosynthesis. The loss of pigment, and fall in ϕ
II
without an accompanying fall in F
v
/F
m
, might be
used as early signs of cadmium poisoning. It is assumed that Cu
2+
was less harmful than Cd
2+
because of
its tendency to remain in roots and because, as a fairly abundant essential micronutrient, it is subject to
endogenous mechanisms of regulation.
© 2011 Elsevier B.V. All rights reserved.
1. Introduction
Heavy metal toxicity in soil was once a problem limited to cer-
tain localities affected by mining, heavy industry, or natural mineral
outcrops. Growing industrialization and the massive use of fer-
tilizers and other agrochemicals in conventional agriculture have
led to its now being of quite widespread concern for both natu-
ral and agricultural systems (Wagner, 1993; Weisberg et al., 2003).
Heavy metal toxicity not only reduces productivity but also threat-
ens the food chain (Poschenrieder and Barceló, 2004). Among the
most common heavy metal pollutants, and the most susceptible to
accumulation through unwary agricultural practices, are cadmium
and copper.
Cadmium is perhaps one of the most aggressive and persistent
of heavy metals. Its presence in the environment is due mainly to
the application of cadmium-bearing phosphorus fertilizers to agri-
cultural soils (Zawoznik et al., 2007). It is not required for life, but
is readily absorbed by the roots of plants and transported to their
aerial parts. It can interfere with plant physiology causing stunt-
ing, root damage and chlorosis (Semane et al., 2007). It mainly
affects the transport and use of water and essential elements (Ca,
Fe, Mg, P and K), causing nutritional and hydric imbalance and
∗
Corresponding author. Tel.: +34 986812616; fax: +34 986812556.
E-mail address: adela@uvigo.es (A.M. Sánchez-Moreiras).
reducing respiration, photosynthesis, and leaf chlorophyll content
(Poschenrieder et al., 1989; Rodríguez-Serrano et al., 2008; Sandalio
et al., 2001; Singh and Tewari, 2003). It can cause oxidative stress
by promoting the peroxidation of membrane lipids or the carbony-
lation of proteins (Rodríguez-Serrano et al., 2008; Romero-Puertas
et al., 2002; Sandalio et al., 2001). The levels of antioxidant enzymes
– superoxide dismutases (SOD), glutathione reductase (GR), cata-
lase (CAT), ascorbate peroxidase (APX) and other peroxidases (POD)
– are altered by cadmium to an extent that depends on the cad-
mium content of the growth medium, the duration of exposure,
the growth stages of plants or organs and the species and tissue
in question (Benavides et al., 2005; Rodríguez-Serrano et al., 2008;
Sandalio et al., 2001).
Copper is an essential micronutrient that acts as a cofactor
in photosynthesis, respiration, ethylene sensing, and lignification
(Jonak et al., 2004), as well as playing roles in the response to oxida-
tive stress (Himelblau and Amasino, 2000). However, excess copper
is toxic for most plants, reducing growth, affecting thylakoid mem-
brane structure, inhibiting root elongation, altering cell transport,
and modifying metabolite levels (see, for example, Schiavon et al.,
2007). As a redox metal capable of catalysing reactions of Fenton
or Haber–Weiss type, it takes part in the direct formation of ROS
(Drazkiewicz et al., 2007; Yruela et al., 1996).
Early detection of heavy metals in plants may hopefully allow
the application of measures that prevent their further accumulation
and their incorporation in the food chain (Ferrat et al., 2003; Van
0098-8472/$ – see front matter © 2011 Elsevier B.V. All rights reserved.
doi:10.1016/j.envexpbot.2011.12.017