chapter 46 - plant roots under aluminum stress - toxicity and tolerance
TRANSCRIPT
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46
Plant Roots Under Aluminum Stress: Toxicity and Tolerance
Hideaki MatsumotoOkayama University, Okayama, Japan
I. DISTRIBUTION OF ACID SOILS AND
THEIR NATURE
Acid soils occupy 3.95 billion ha (30%) of the worlds
ice-free land area (Baligar et al., 1998), comprising
both the tropical and temperate belts. The distribution
of acid soil in selected regions in the world is shown in
soil acidity, acid soil can be classified into 10 groups.
Oxisols and Ultisols are the major acid soils in the
tropical region and occupy 22% (846 m ha) and 18%
(727 m ha), respectively, of the acid soil area in theworld. Inceptisols including the sulfate soils of many
tropical river deltas are very acidic owing to acid
formed upon oxidation of sulfides. The level of acid-
ification of acid soil generally reflects the degree of
weathering and leaching it has experienced (Baligar
et al., 1998). In addition to the natural factors that
affect weathering, agricultural farming processes such
as the excessive supply of inorganic fertilizers or
removal of cations by harvest lower the pH.
Furthermore, the acidity of soils is gradually increased
owing to environmental pollution and acid rain. Acid
soils are infertile because they lack the basic nutrients,
such as Ca2, Mg2, and K. Acid soils are character-
ized by high content of toxic elements such as Al, Mn,
and Fe or deficiency of Ca2, Mg2, K, N, and P.
Most acid soils have low cation exchange capacity,
leading to loss of essential minerals and to poor crop
production.
II. ALUMINUM TOXICITY IN ACID SOILS
A. Occurrence and Chemistry of Al
Exchangeable Al and Mn are the major toxic elements
in most acid soils. In most Oxisols and Ultisols, Al
occupies 494% of the cation exchange sites (Baligar
et al., 1998). Al is the most abundant metal in the
earths crust.
Aluminum exists in the soil in insoluble aluminosi-
licates or oxides. It has complicated chemical form and
biological function. At pH < 5, Al3 exists as the octa-
hedral hexahydrate, AlH2O36 , often abbreviated as
Al3. As the solution becomes less acidic, AlH2O36
undergoes successive deprotonations to yield
AlOH2 and AlOH2 . In neutral solution AlOH3precipitates as gibbsite which redissolves in basic solu-
tions owing to formation of tetrahedral AlOH4 as
aluminate anion. Time-dependent formation of poly-
nuclear species may also take place (Martin, 1986).
Since Al toxicity differs with the chemical form of Al,
many studies have been done regarding this interac-
tion, especially between Al3 and mononuclear
hydroxy-Al. Generally Al3
is more phytotoxic thanAlOH2 or AlOH2 , but Alva et al. (1986) and
Kinraide and Parker (1987) reported that dicotyledo-
nous plants may be more sensitive to AlOH2 and
AlOH2 than to Al3. The difference in behavior of Al
species between monocots and dicots may be related to
the fact that dicots have a much higher CEC in their
821
Copyright 2002 by Marcel Dekker, Inc.
Table 1. Depending on the degree of weathering and
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cell wall than monocots, but further studies are needed
to elucidate the cause.
In the soil solution Al3 reacts not only with OH
but also with phosphate, F, SO24 , silicate, and a large
number of organic ligands. Under specific conditions
of OH/Al ratio, total Al, and stirring rate,AlO4Al12OH24H2O712 (Al13 polymer), which is
highly toxic, can be formed (Parker et al., 1989).
Nevertheless, Al13 was not observed in soil solutions
(Funakawa et al., 1993). Rhizotoxicity of the alumi-
nate ion, AlOH4 , which is formed at an alkaline
pH was tested with wheat and red clover. Root elonga-
tion was inhibited to < 4% by 25M AlOH4 at pH 8
but not at pH 8.9, where elongation was unaffected.
Thus, AlOH4 is nontoxic, and the inhibition at a
lower pH is attributable to the Al13 formed
(Kinraide, 1990).
B. Inhibition of Root Elongation by Al
Inhibition of root elongation is the first visible symp-
tom of Al stress. In most plant species, root elongation
is markedly inhibited by Al at the mol level in a
simple solution containing Ca2 alone. Inhibition of
root elongation of Al-sensitive maize occurred within
30 min of Al treatment (Llungany et al., 1995).
However, inhibition of root elongation is reduced in
the presence of other ions, because the interaction with
other coexisting ions reduces the toxicity of Al3.
Changes in the electric charge of the root surface by
other ions, especially cations, affect the accessibility of
Al3. Root elongation in Al-sensitive wheat cultivar,
Scout 66, was apparently inhibited by a 3-h treatment
with 5M Al, but that of Atlas 66 was inhibited to the
same degree only by a 10-fold higher concentration of
elongation zone) accumulated more Al and plays a
major role in the Al perception mechanism.
Indeed, only the apical 23 mm of maize and pea
roots need to be exposed to Al for the inhibition of
root elongation to take place (Delhaize and Ryan,
1995; Matsumoto et al., 1996). In near-isogenic
wheat (Triticum aestivum) lines differing in Al toler-
ance, root apices of Al-sensitive genotypes were stainedwith hematoxylin after a short exposure to Al (10 min
h). Apices of Al-tolerant seedlings showed less inten-
sive staining (Delhaize et al., 1993a). This indicates
that inhibition of root elongation by Al varies among
plant species or cultivars. Similar results were obtained
with Al-tolerant wheat (Atlas 66) and Al-sensitive
wheat (Scout 66) exposed to Al for 1 day (Sasaki et
differences in Al accumulation in the root apex are
related to differences in Al sensitivity, (2) inhibition
of root growth is related to the Al content in the
root apex, and (3) tolerant cultivars possess a mechan-ism that excludes Al from root apices (Rinco n and
Gonzales, 1992; Samuels et al., 1997).
1. Morphological Changes of Intact Roots andRoot Cells Under Al Stress
Accumulation of coating materials on the epidermis of
the apex and around the cap is commonly observed
upon Al stress. Root meristem cells of canola
(Brassica napus var. napus L. cv. barassa) plants,
grown under control conditions, responded differently
from the much larger control cap cells (Clune and
Copeland, 1999). Under mild Al stress (20M, 24 h),
these cells expanded and increased in number, but
under more severe treatment (80M Al, 24 h) they
diminished in size and number. Furthermore, the dis-
tinct boundary between cells in the root cap meristem
and the elongation zone was no longer apparent, and
the outer layer of cells in the root cap appeared to be
only loosely attached. After only 4 h in 80M Al,
many ultrastructural changes were evident in periph-
822 Matsumoto
Table 1 Extent of Acid Soils in the World and Selected Regions a
Distribution class Global
Region
Central
America
South
America Africa AsiabAustralia/
New Zealand
North
America Europe
Acid land area (106 ha) 3,950 37 917 659 532 239 662 391
Acid land area (%)c
30 35 14 22 76 30 30 37aVon Uexkull and Mutert (1995).bExcluding South and East Asia.cIce-free land area of the globe.
Source: Baligar et al. (1998).
Copyright 2002 by Marcel Dekker, Inc.
Al (Fig. 1). The root apex (root cap, meristem, and
al., 1997b) (Fig. 2). These results suggest that (1) the
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eral root cells, including the appearance of numerous
small vacuoles that occupied most of the cytoplasm.
After 24 h, disorganization of the cellular contents of
the peripheral root cap cells became obvious, and the
plasma membrane was clearly separated from the cell
wall. The cytoplasm was markedly reduced in volume
and extensively vacuolated. Similarly, Al-induced
vacuolations have been observed in several plant spe-cies (Ikeda and Tadano, 1993; Marienfeld et al., 1995).
In Lemna minor, the vacuolation and numerous mye-
linlike whorls of membrane increased in the apical
meristem of the root (Severi, 1991). Moreover, the vesi-
cles produced by the Golgi apparatus were larger.
However, whether vacuolation is related to the storage
of Al remains to be determined.
Al has a localized effect on auxin transport and
unilateral application of Al inhibited root curvature.
Inhibition of cell elongation in the elongation zone is
the major outcome of the inhibition of root elongation.Shortening of the root elongation zone by Al is accom-
panied by an increase in the diameter and a decrease of
the length of the cells in the second and third layers of
the cortex of the elongation zone of Atlas 66 plants
(Matsumoto, 2000; Sasaki et al., 1996)
The ratio of length to diameter of the cells in the con-
trol root was three to four times larger than that in the
Al-treated roots, and cells in the second and third
layers of the cortex were swollen laterally.
The Al-induced inhibition of longitudinal cell
expansion and cell swelling in the elongation zone
might be related to the disorder of the cytoskeletalnetwork. The orientation of the microtubules (MTs)
is closely related to cell expansion. Longitudinally
elongating cells have transversely oriented MTs. MT-
disrupting agents promote lateral expansion but inhibit
longitudinal expansion. Cortical MTs are known to be
involved in the orientation of cellulose microfibrils.
Indeed, the disappearance of the cortical MTs in elon-
gating cells of wheat roots that was observed under Al
stress (Sasaki et al., 1997a) might be responsible for
these changes in cell growth. Moreover, the time-
dependent effect of Al on MTs stability was correlated
with that on the reduction of root growth.
The effect of Al on the behavior of structural pro-
teins has been investigated intensively in recent years.
The actin network plays an important role in the plant
cell. Al induced a significant increase in the tension
within the transvacuolar actin network in soybean
cells (Grabski and Schindler, 1995). Al resulted in a
reorganization of MTs in the inner cortex, but not
outer cortex, and in the epidermis of the elongation
zone of Zea mays (Blancaflor et al., 1998). They also
Aluminum Stress 823
Figure 1 Time course for wheat root elongation of Atlas 66
and Scout 66. Seedlings were in the presence and absence of 5
(Scout 66) or 50 (Atlas 66) M Al. Data are means (SE) of
results from 10 roots. (From Sasaki, 1996.)
Figure 2 Hematoxylin-stained wheat roots of Atlas 66 and
Scout 66. Seedlings were grown in the presence and absence
of Al for 48 h. (From Sasaki et al., 1997b.)
Copyright 2002 by Marcel Dekker, Inc.
(Figs. 3, 4).
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824 Matsumoto
Figure 3 Photomicrographs of longitudinal sections of wheat roots of Atlas 66. Roots were treated with or without 20 M Alfor 24 h. Bar indicates 0.2 mm. (From Sasaki et al., 1996.)
Figure 4 Effects of Al on the lengths and diameters of wheat root cells in the second layer from surface in Atlas 66. Roots were
treated with or without 20M Al for 24 h (a) or 48 h (b). Data are means (SE) of results from five or six samples. (From Sasaki
et al., 1996.)
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found that the auxin-induced reorientation and cold-
induced depolymerization of MTs in the outer cortex
were blocked by Al, suggesting that Al increased the
stability of MTs in these cells. The changes of behavior
of MTs against Al stress may depend on the growth
phase of the cells (Sivaguru et al., 1999). This stability
effect of Al in the outer cortex coincided with growth
inhibition. Aluminate [AlOH4 ] at pH 10.0 inducedthe bending of roots of salt-tolerant grass
(Thinopyrum bessarabium A. Lo ve). The roots under
aluminate treatment displayed a number of morpholo-
gical and structural malformations (Eleftheriou et al.,
1993). The root cap decreased in size, and both the
calyptrogen and the meristemic region occupied a
smaller area. Amyloplasts in the root cap cells were
hardly distinguishable and showed less evidence of
sedimentation.
The swollen cells of wheat roots were characterized
by the drastic accumulation of lignin on their cell wallsunder Al stress (Sasaki et al., 1996). The decrease of
cell viability of the elongation zone of wheat roots were
also observed after 3 h of exposure to Al which coin-
cided with the time required for the inhibition of the
root elongation as well as for lignin deposition (Sasaki
et al., 1997b). It is still unknown whether lignin deposi-
tion is involved in the mechanism of Al toxicity. The
morphological changes in roots were characterized by
the cracks on the root surface (Sasaki, 1996) (Fig. 5).
Cracking might be caused by the outward pressure of
the cells in the second and third layers of the cortex of
wheat roots. The distal part of the elongation zone ofmaize roots, where cells are undergoing a preparatory
phase for rapid elongation, is the primary target of Al
influence (Sivaguru and Horst, 1998).
To understand the primary event of Al toxicity, we
must know how the cells in the specific zones, i.e.,
elongation and/or transition zone of the root, accumu-
late Al and how their elongation is inhibited by ultra-
structural alterations. Why do such events cause death
of the cell? In other words, are the matured root cells
resistant to Al toxicity after their elongation has
ended?
2. Inhibition of Cell Division
Cell division in root meristems of several plants is
inhibited by Al (Clarkson, 1965; Morimura et al.,
1978). However, cell division accounts for only 12%
of the overall root elongation. Furthermore, cell cycle
in plants takes about 1 day. However, the primal phe-
nomenon of Al toxicity is the inhibition of root elon-
gation that occurs within hour(s) of Al treatment.
Thus, attention has been largely paid to the inhibitionof root cell elongation as the primary site of Al toxi-
city.
On the other hand, the lethal consequence of Al
toxicity might be inhibition of cell division
(Matsumoto, 2000). Large amounts of Al accumulate
in the developing lateral roots of pea roots where cells
are actively dividing (Matsumoto et al., 1976a). Al was
detected in nuclei of root hair cells by staining and by
chemical determination of Al in purified nuclei pre-
pared from Al-treated pea roots. Furthermore, Al
accumulation in the nuclei of soybean root tips was
detected with Al-sensitive stain lumogallion and con-
focal laser scanning microscopy (Silva et al., 2000). The
nuclei isolated from pea roots treated with 1 mM AlCl3at pH 5.5 for 1 day were fractionated; 73% of the total
Al in nuclei was recovered in the chromatin fraction,
and 94% of Al in chromatin was recovered in DNA
(Matsumoto et al., 1977b).
Expression of genetic information of DNA is regu-
lated by structural changes of DNA and chromatin.
Unwinding of double strands of DNA is a prerequisite
Aluminum Stress 825
Figure 5 Photographs with scanning electron microscope of
wheat root surface of Atlas 66. Roots were treated without
and with 50M Al for 4 h in the presence of 0.1 mM CaCl2.
(From Sasaki, 1996.)
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for expression of genetic information, but separation
of double strands of DNA was interrupted by Al (Fig.
6) (Matsumoto, 1991). Furthermore, the structural
change of chromatin in pea roots treated with Al in
vivo implied that Al induced the condensation and/or
aggregation of chromatin (Matsumoto, 1988). These
results suggested that the template activity of DNA
and/or chromatin of pea roots for RNA synthesis isrepressed by Al. This is caused by Al-induced struc-
tural alteration of DNA and chromatin through the
association of the negative charge of phosphates of
DNA and positively charged Al3 (Morimura and
Matsumoto, 1978). Plant cells require dynamic cytos-
keleton-based networks for various cell activities (e.g.,
differentiation and division). With suspension of
tobacco cells, Sivaguru et al. (1999) found that the
actively dividing log-phase cells were characterized
with faint and larger phragmoplasts and unusually
enlarged daughter nuclei after 6 h of Al treatment.
After a 24-h treatment, no phragmoplasts and spindle
MTs (SMT) from cells having metaphase plate chro-
mosomes were observed.
The disintegration of SMT and disorganization of
phragmoplasts caused by Al might block cell divisiondirectly at the metaphase. As mentioned before, inhibi-
tion of cell division will be the cause for the complete
inhibition of root elongation by Al and subsequent
death. Therefore, elucidation of the detailed mechan-
ism of cell division inhibition by Al will be required in
order to understand the mechanism of Al toxicity
(Matsumoto, 2000).
C. Site of Al Toxicity
1. Apoplast
Although there is disagreement with regard to the site
of Al toxicity, namely, symplastic or apoplastic, many
investigators have stated that 3090% of the absorbed
given to the role of CEC in connection with Al accu-
mulation in the apoplast. On the one hand, high CEC
will be associated with large quantities of Al accumu-
lated in the apoplast. On the other hand, high CEC
may prevent Al from entering the symplast, where it
exerts its lethal effect. However, a clear relationship
between root CEC and Al sensitivity and/or tolerancewas not found across a wide range of plant genotypes
(Grauer, 1992).
As to the binding site of Al in the apoplast, pectin
carboxyl was suggested as a plausible candidate
although almost no evidence has been found to show
the binding of Al to pectin in vivo (Matsumoto et al.,
1977a; Horst, 1995). Although Al is bound by the
negative charge of pectin, the binding capacity of pec-
tin varies with the plant species, and the pectin content
is extremely different between monocots and dicots.
Even in the same species, the pectin content of the
roots differs with the position on the root or with the
chemical modification of pectin, such as methylation
or demethylation changes with the physiological activ-
ity of the cell. A Ca-pectate membrane was used as a
model system. There was a rapid reaction between Al
and Ca pectate, but there was no difference in Al
remaining in solution even after 16 min. Only a slight
decrease was observed after 24 h. The solution contain-
ing 29M Al and 1 mM Ca reduced the flow through
the Ca pectate membrane by > 80% compared to the
826 Matsumoto
Figure 6 Proposed mechanism of inhibition of the tran-
scription of RNA by Al. (A) Normal transcription of RNA
on a sense strand of DNA template in the absence of Al. A
short section of the double strands must open and, thus, only
the sense strand can act as the template. (B) Transcription is
inhibited in the presence of Al. Sections of the double strands
(indicated by two arrows) are captured by Al polymers with
various structures shown as Al Al Al, through the
strong electrostatic interaction between phosphate groups
with a negative charge and the large positive charge of the
Al polymer. Thus, separation of the strands is blocked and
limited synthesis of RNA results. In addition, the Al polymer
with its large positive charge on one helix, shown as nAlm
where n and m are highly variable and depend on coexisting
factors, can associate with the other helix and cause aggrega-
tion of chromatin fibers. (From Matsumoto, 1991.)
Copyright 2002 by Marcel Dekker, Inc.
Al is localized in the apoplast (cf. Tice et al., 1992;
Rengel, 1996). Two possible interpretations has been
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solution containing 1 mM Ca only. These results sug-
gest that an important effect of toxic Al is a reduction
in water movement into roots (Blamey et al., 1993).
Interactions of Al with other cell-wall components,
such as enzymes, extensin and xyloglucan may affect
the functional integrity of cell walls. In the roots of
cotton seedlings, Al impaired the sucrose utilization
for cell wall formation (Huck, 1972). Al also inducedthe production of cell-wall components of squash seed-
lings, especially of hemicellulose, (Van et al., 1994).
Al stress increased the level of covalently bound cell
wall proteins in pea roots (Pisum sativum cv. Alaska).
In vitro and in vivo Al binding experiments have
suggested that extensin has the highest capacity to
bind Al among cell wall proteins (Kenjebaeva et al.,
2001).
2. Plasma Membrane
The plasma membrane is one of the first targets of Al
(Haug, 1984; Matsumoto, 2000). Al binds readily to
the plasma membrane because of its high content of
phosphate such as phospholipids and the negative
charge of the membrane surface. Al3 has a 560-fold
higher affinity for the phosphatidyl choline surface
than Ca2 (Akeson et al., 1989). Structural and func-
tional changes of the plasma membranes are induced
by Al binding, although the evidence of Al binding to
the plasma membrane in vivo is limited (Matsumoto et
al., 1992). Al-induced changes in membrane behavior
of intact root cortex cells ofQuercus rubra root showedthat Al altered the activation energy required to trans-
port water (32%), urea (9%), and monoethyl urea
(7%) across cell membranes as measured by the plas-
mometric method (Zhao et al., 1987). Al increased the
lipid partiality of the plasma membrane at > 9C but
decreased it at temperatures < 7C. These changes in
membrane behavior are explainable if Al reduces mem-
brane lipid fluidity and kink frequency and increases
packing density and the occurrence of straight lipid
chains (Chen et al., 1991). It can be concluded that
Al3 (1) increased membrane permeability to the none-
lectrolytes, (2) decreased the membrane partiality for
lipid permeators, and (3) decreased membrane perme-
ability to water caused by increased activation energy.
It is thus implied that Al3 alters the architecture of
membrane lipids (Vierstra and Haug, 1978).
Furthermore, Al3 inhibited the influx of cations
and enhanced the influx of anions. This was caused
by the Al-induced formation of positively charged
layer at membrane surface influencing ion movement
to the binding sites of the transport proteins. A posi-
tively charged layer would retard the movement of
cations to the plasma membrane. This is explained
by the charge of the membrane surface potential,
Zeta potential, through the binding of Al. It was also
argued from the relationship between Al tolerance and
surface negativity of plasma membranes (Wagatsuma
et al., 1995). Al reduced the negative charge associated
with phospholipids, i.e., depolarization of Zeta poten-tial, and proteins by binding to these charged groups
or shielding the surface charges. Alteration of K
efflux and H influx by Al also affect the Zeta potential
as well as the potential difference (PD) across plasma
membrane (Sasaki et al., 1994a).
A more direct effect of Al3 is its binding to trans-
port proteins and impairs their function. For instance,
Al3 blocks inward-rectifying K channels in root
hairs of wheat (Triticum aestivum) and VDAC, chan-
nel-forming protein located in the outer mitochondrial
membranes (Dill et al., 1987). Recently, a special inter-action was found between depolarization of Zeta
potential and decrease of H
-ATPase of plasma mem-
brane of squash roots treated with Al. The interaction
was typically observed at root tips, 05 mm portion of
the root (Ahn et al., 2001). However, the varietal sen-
sitivity to Al3 is not based on the difference in cell
surface electrical potential (Kinraide et al., 1992), and
inhibition of root growth by Al is not caused by the
reduction in current or H+ influx at the root apex
(Ryan et al., 1992). On the other hand, a different
membrane potential depolarization of root cap cells
preceded Al tolerance in snapbean (Phaseolus vulgarisL.) (Olivetti et al., 1995). The Al-tolerant cultivar Dade
depolarized rapidly upon exposure to Al, but the Al-
sensitive cultivar Romano was only slightly depolar-
ized. This might be related to the fact that Al reduces
the K efflux channel conductance in the tolerant
Dade root cap cells, but does not affect it in the sensi-
tive cultivar Romano. Further research is needed to
understand the interrelationship between Al toxicity
and/or tolerance and electrophysiology.
One of the biochemical changes of the plasma mem-
brane is the Al-dependent lipid peroxidation in the
root tip of soybean (Glycine max). A close relationship
existed between lipid peroxidation and inhibition of
root elongation induced by Al and/or Fe toxicity
and/or Ca deficiency (Cakmak and Horst, 1991).
Enhanced lipid peroxidation by oxygen free radicals
can be a consequence of primary effects of Al on mem-
brane structure. The tolerance mechanism against Al
toxicity in terms of lipid peroxidation was proposed for
tobacco suspension cells (Yamamoto et al., 1998).
Lipid composition can be a determinant of the varietal
Aluminum Stress 827
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in the free Ca2 concentration and triggering callose
synthesis cannot be excluded.
Ca2 may not be the only signal for callose forma-
tion, and alteration in the plasma membrane architec-
ture might also be important for callose synthesis
(Jacob and Northcote, 1985). As callose is released
into the apoplast after its synthesis on the plasma
membrane, cell walls of root cells of Al-treated plantsmost likely contain callose depositions.
What is the inhibitory function of callose under Al
stress? Callose can be considered as a sealing system
in plants. Callose is localized in the wall around the
plasmodesmata, which appear to be structurally sub-
divided. Thus, the constricting force upon callose
synthesis would be transmitted to the plasmodesmal
core (Turner et al., 1994). This will inhibit the trans-
port of cellular compounds through plasmodesmata
under Al stress. A large increase of callose accumula-
tion at the plasma membrane under Al stress wasfound in Al-sensitive wheat roots. Such an increase
inhibited the cell-to-cell trafficking of molecules
through the plasmodesmata, resulting in the inhibi-
tion of root elongation. Furthermore, these events
are markedly repressed in the presence of 2-deoxy-
D-glucose, which is a callose synthase inhibitor
(Sivaguru et al., 2000). However, in an Al-tolerant
Arabidopsis mutant, no direct relationship between
Al uptake and callose formation was established
(Larsen et al., 1996).
D. Signal Transduction and Al Signal
Plants respond to Al stress quickly. Inhibition of root
elongation is observed within less than an hour, and
homeostasis of cytoplasmic free Ca2 is broken
instantly after Al addition. Special attention has been
paid to phosphoinositide-associated signal transduc-
tion. AlCl3 and Al-citrate inhibited phospholipase C
(PLC) of the microsomal membrane in a dose-depen-
dent manner in wheat roots. I50 was observed at
1520M Al (Jones and Kochian, 1995). Binding of
Al to microsomes and liposomes was found to be lipid
dependent, with the signal transduction element PIP2having the highest affinity for Al with an Al:lipid stoi-
chiometry of 1:1. These results suggest an Al effect on
the signal transduction pathway that is associated with
the mechanism of Al toxicity.
How is the Al signal recognized by receptor and
how is it transported into the cytoplasm at the root
apices? Bennet and Breen (1991) proposed that the
Al signal is perceived in the root cap of Zea mays.
Matsumoto et al. (1996) speculated that the transduc-
tion of Al signal in barley roots is related to an increase
of ABA. ABA induces both the ATP- and PPi-depen-
dent H pump activity of the tonoplast (Matsumoto et
al., 1996). Contrary to ABA, transport of exogenously
applied [3H]indole-3-acetic acid to the meristemic zone
was significantly inhibited by Al in maize roots. The
signaling pathway in the root apex mediating the Al
signal may be responsible for the genotypic differencein Al resistance (Kollmeier et al., 2000). The biochem-
ical mechanism in terms of the transduction of Al sig-
nal is poorly understood. Protein phosphorylation may
be involved because of the strong association of Al
with phosphate.
E. General Metabolism Affected by Al
The effect of Al on excised root apices and isolated
mitochondria of wheat was investigated. O2 uptakeby excised roots was reduced by 23% and 35%
after 12- and 24-h treatment with 75M Al.
Mitochondria isolated from Al-treated roots had
reduced oxidative capacity with supply of electrons
to complexes I and II. It was found that initially Al
affected electron flow through complexes I and II,
and after longer exposure interacted with other sites
in the mitochondria (de Lima and Copeland, 1994).
Al tolerance of Phaseolus vulgaris (cv. Dade) was an
inducible trait. In this cultivar, the resumption of root
elongation during recovery from Al treatment was
accompanied by increased rates of respiration.Respiration rates slowly declined over the 72-h treat-
ment of Al-sensitive Romano. When partitioned into
growth and maintenance expenditures, a larger pro-
portion of root respiration of Al-treated Dade plants
was allocated to maintenance processes, potentially
reflecting diversion of energy to metabolic pathways
that offset the adverse effects of Al toxicity (Cumming
et al., 1992).
Carbon metabolism is also affected by Al. Al stress
increased alcohol dehydrogenase activity in wheat
(Triticum aestivum cv. Vulcan) roots. Sucrose synthase
and lactate dehydrogenase were also increased in Al-
treated roots, suggesting that the early effect of Al on
wheat roots may be a shift from aerobic to anaerobic
metabolism. The first two enzymes in the pentose phos-
phate pathway (G-6-PDH and 6-PGDH) decreased in
Al-sensitive wheat cv. Grana. However, these two
enzymes first increased, but then decreased in Al-toler-
ant rye (Sla ski et al., 1996). These results suggest that
the mechanism of Al resistance involves the regulation
of the pentose pathway.
Aluminum Stress 829
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III. ALUMINUM TOLERANCE MECHANISM
A. Al Tolerance on Genetic Basis
The bimodal distribution of phenotypes corresponding
to 3:1 segregation ratio for Al tolerance/sensitivity in
populations derived from crosses between tolerant and
sensitive cultivars revealed the presence of single majorgenes for Al tolerance (Gain, 1998). In addition to
major genes conferring major differences in Al toler-
ance, there is also some evidence that minor genes or
modifier genes may play a role in modulating the effect
of major Al tolerance genes. Other studies have sug-
gested that genetic factors located on the long arm of
chromosome 2D prevent accumulation of Al in root
apical meristems of the BH1146 euploid wheat (Aniol,
1995). However, other genetic factors are also located
on these chromosome segments that control Al detox-
ification in the root tips of Al-tolerant lines.
The D genome of wheat may determine the toler-ance to acid soil and consequently contribute to the
increased adaptation of hexaploid wheats during
their evolution. Atlas 66 is a well-known Al-tolerant
cultivar of wheat. However, not all the genes for tol-
erance to Al in Atlas 66 are located on the D genome
chromosome (Berzonsky, 1992). Furthermore, Al tol-
erance in wheat is a dominant trait and the majority of
observed variability could be explained by hypotheses
of two or three gene pairs, each gene affecting the same
character with complete dominance of each gene pair.
Al tolerance in the ditelosomic line of Chinese Spring
wheat cultivar revealed that genes controlling this
character are located on the short arm of chromosome
5A and the long arm of chromosomes 2D and 4D
(Delhaize et al., 1993a).
Conservation of the Al tolerance gene by various
species was investigated. RFLP markers for a major
wheat Al tolerance gene AltBH were found on the long
arm of chromosome 4D, while in rye, the Al tolerance
gene was located on chromosome 4, which harbors
chromosome segments homologous to regions of
wheat chromosome 4D. In barley, the Al tolerance
gene Alp is almost certainly orthologous to the wheatAltBH gene due to the fact that the relative positions of
Alp and AltHB with respect to a common set of mole-
cular markers are virtually identical in both genomes
(Berzonsky, 1992). In spite of efforts made so far, the
genetics of Al tolerance is little known for any single
species. As to the physiological functions of Al toler-
ance genes, Delhaize et al. (1993b) found that Al tol-
erance, controlled by the Alt gene in wheat, appeared
to be dominant across a range of Al concentrations
based on identical Al tolerance in heterozygotes and
Alt 1 homozygotes. This gene controls the excretion of
malate upon Al stress.
B. Genetic Basis of Al Tolerance
Application of lime to acid soils to increase the soil pHis one strategy for alleviating Al toxicity. However, this
technique is problematic from the economical and
environmental points of view. Another strategy is to
use Al-tolerant crops. Breeding may depend on classi-
cal techniques and/or transgenic plants to which Al
tolerance genes are being introduced. Snowden et al.
(1995) isolated several cDNA (wali 17) whose tran-
script accumulates in wheat under Al treatment. A
cDNA library constructed from the mRNA of Al-trea-
ted roots of Al-sensitive wheat (cv. Victory). It was
screened with a degenerate oligonucleotide probe
derived from a partial amino acid sequence of theAl-induced protein TAl-18. Out of seven clones that
initially hybridized with the probe, one encoding a
novel 1,3--glucanase mRNA was upregulated in Al-
treated roots, with highest expression after 12 h. A
second cDNA showed similarity to genes encoding
cytoskeletal fimbinlike protein. Unfortunately, a trans-
genic protein enriched with those genes was not con-
structed (Cruz-Ortega et al., 1997). Al ions bind to
phospholipids, and the plasma membrane is a primary
barrier to the entry of Al into the cells (Matsumoto,
1988; Kochian, 1995). Thus, a change in lipid compo-
sition of the plasma membrane could improve the
resistance of the cell by excluding Al (Delhaize et al.,
1999). Cloned wheat cDNA (TaPSS1) that codes for
phosphatidyl serine synthase (PSS) was tested.
Overexpression of PSS increased Al resistance in
yeast. However, a high level of TaPSSI expression in
Arabidopsis and tobacco led to the appearance of
necrotic lesions on leaves, which may have resulted
from the excessive accumulation of PS (Delhaize et
al., 1999). An Arabidopsis blue-copper-binding protein
gene, a tobacco glutathione S-transferase gene, a
tobacco peroxidase gene, and a tobacco GDP dissocia-tion inhibitor gene conferred a certain degree of resis-
tance to Al (Ezaki et al., 2000). These lines also showed
increased resistance to oxidative stress, suggesting a
link between Al stress and oxidative stress in plants.
One successful approach was the generation of
transgenic tobacco and papaya with the citrate
synthase (CS) gene from Pseudomonas aeruginosa
with the 35S promoter of cauliflower mosaic virus
introduced using a Ti plasmid derived from a transfor-
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mation system. The idea was that organic acids serve
as chelating agents and may prevent Al toxicity
(Delhaize and Ryan, 1995; Fuente et al., 1997).
Hematoxylin staining was employed to examine
whether the increased Al tolerance of the CSb lines is
due to the inhibition of Al uptake by the root tip.
Following exposure to Al CSb lines showed a consid-
erably lighter staining than the control. Apparently,the expression of a citrate synthase in the cytoplasm
increases the concentration of citrate, which led to a
higher rate of its efflux; the higher synthesis and excre-
tion of citrate confers Al tolerance.
C. Organic Acids as Al-ChelatingSubstance
Since higher plants cannot move away from the acid
soil, they have developed ways to reduce this edaphicstress. An effective strategy to reduce the stress is to
chelate the Al3
in the rhizosphere and by that reduce
its toxicity. Exclusion of malate from wheat (Delhaize
et al., 1993b); citrate from maize, Cassia tora, and rye
(Miyasaka et al., 1991; Zheng et al., 1998; Li et al.,
2000b); and oxalic acid from taro and buckwheat
(Ma and Miyasaka, 1998; Ma et al., 1997b) have
been reported. Some plants exclude both malate and
citrate under Al stress. Malate and oxalate are excreted
instantly under Al stress, but citrate is excreted only
after a lag phase. These results suggest that stored
malate and oxalate are excreted while citrate is synthe-sized by a gene-regulated system.
The organic acids were classified into three groups
of Al detoxifiers: (1) strong (citrate, oxalic, tartaric);
(2) moderate (malic, malonic, salicylic); and (3) weak
(succinic, lactic, formic, acetic phthalic) (Hue et al.,
1986). The following facts support the role of excreted
organic acids as detoxifiers; During the first 20 h of Al
exposure, the root growth rate of both tolerant and
sensitive maize varieties was severely inhibited.
However, after this period, root growth was resumed
in the tolerant plants, but remained severely inhibited
in the Al-sensitive one. A dose-dependent citrate and
malate exudation was observed from tolerant but not
from sensitive roots (Jorge and Arruda, 1997; Yang et
al., 2000). The root of the Al-resistant snapbean
released 70 times more citrate in the presence of Al
as in its absence, and the amount of citrate excreted
was 10 times as much as that of Al-sensitive cultivars
(Miyasaka et al., 1991). Similar results regarding
malate exclusion were obtained with Al-tolerant and
Al-sensitive isogenic wheat lines.
In > 36 lines of wheat cultivars differing in Al resis-
tance that were screened, Al-stimulated malate release
was correlated with Al resistance (Ryan et al., 1995). It
was shown that addition of organic acids to the solu-
tion ameliorated Al toxicity in the root of Al-sensitive
varieties and reduced dramatically the loss of viability
of root cells (Li, 2000). This may be explained by the
fact that complexes of Al with di- and tricarboxylicacids were not transported through root cell mem-
branes (Ma et al., 1998). Excretion of organic acids is
Al3 specific and is not induced by other trivalent
cations (Ma et al., 1997b).
The loss of a certain chromosome arm resulted in a
decrease in Al resistance in ditelosomic wheat lines and
decreased rates of root apical malate release concomi-
tant with decreased Al exclusion (Kochian, 1998).
Exposure to Al induced depolarization of the mem-
brane potential (Em) in Al-tolerant wheat cultivars
but not in an Al-sensitive cultivars. Depolarizationwas specific to Al. Al-induced depolarization of root
cap cell membrane potentials is probably linked to
malate release (Papernick and Kochian, 1997).
Al3 triggers the opening of the putative malate-
permeable channel. Several antagonists of anion chan-
nels inhibited the Al-stimulated efflux of malate. The
anion channel antagonist niflumate inhibited the cur-
rent in whole-cell measurements by 83% at 100 M Al.
Patch clamp recordings revealed a multistate channel
with single-channel conductance of between 27 and
66 ps. This is a good candidate to be the transport
system facilitating Al-induced malate release (Ryan etal., 1997b). K-252a, a potent inhibitor of protein phos-
phorylation, reduced dramatically the excretion of
malate from Al-treated wheat, suggesting the involve-
ment of protein phosphorylation for the regulation of
malate excretion under Al stress (Osawa and
Matsumoto, 2001).
Transgenic introduction of the bacterial cytosolic
citrate synthetase gene into tobacco and papaya
resulted in Al tolerance (Fuente et al., 1997).
Excretion of organic acids from the root apex where
Al injury is located seems to be a reasonable strategy
for the effective use of carbon and energy by the plant
(Delhaize and Ryan, 1995). Such experimental evi-
dence indicates that the mechanism of Al exclusion
that depends on the chelation of Al3 with excreted
organic acids is an effective strategy. However, it is
unclear whether the quantities of organic acids released
are adequate to explain the insensitivity to Al of the
more tolerant genotypes. Consumption of the excreted
organic acids by soil bacteria should also be consid-
ered. The question why different plant species excrete
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different organic acids in different ways upon Al stress
also remains to be solved. The efflux of organic acids is
probably switched on or off by the Al3 stress, because
continuous excretion of organic acids from roots
would consume carbon and energy in extraordinary
amounts. The precise mechanism remains to be eluci-
dated, and a more integrative, multifaceted model of
tolerance is needed (Parker and Pedler, 1998).The role of intracellular organic acids on Al toler-
ance was investigated using the Al-tolerant plant
Hydrangea macrophylla. Leaves of hydrangea may
contain up to 15.66 mmol Al kg1 fresh weight.
About 77% of the total Al exists in the cell sap (Ma
et al., 1997a). The ligand in the Al complex of hydran-
gea leaves was citric acid with a molecular ratio of 1 Al
to 1 citrate. The purified Al:citrate complex from
hydrangea leaves did not inhibit the root elongation
of maize and did not decrease the cell viability
although both parameters were strongly inhibited bythe same concentration of AlCl3. This means that Al in
the form of Al:citrate is not toxic. Also, buckwheat
contains large amounts of Al compared to other crop
plants but can grow normally under Al stress. This
suggests that buckwheat can detoxify Al. The measure-
ment of 27Al-NMR revealed that the Al in buckwheat
leaves and roots existed as an Al:oxalate (1:3) complex.
The Al:oxalate (1:3) complex is the least toxic complex
compared to other complexes. Buckwheat contains a
large amount of oxalate regardless of Al stress and can
excrete oxalate immediately after the plant is exposed
to Al. Even if some Al is incorporated into the planttissues, it is immediately chelated there.
D. Protein Expression in Roots Under AlStress
Wheat genotypes differing in Al tolerance were com-
pared for qualitative and quantitative differences of
their proteins. However, no conclusive evidence for
upregulation of a certain protein that confer Al toler-
ance was reported (Delhaize et al., 1991; Ownby and
Hruschka, 1991). Most of the changes in protein
expression associated with Al stress probably result
from the effects of Al on cell metabolism. Another
approach was to look for proteins that are character-
ized by their binding capacity to Al. Appearance of the
23-kDa peptide in root exudates cosegregated with the
Al-resistant phenotype in F2 populations and had a
significant Al-binding capacity (Basu et al., 1999).
Similarly, a 51-kDa membrane-bound protein accumu-
lated in the root tip of Al-tolerant wheat (PT741)
under Al stress. The specific induction of the 51-kDa
band in PT741 suggested a potential role of these pro-
teins in mediating resistance to Al, associated with the
tonoplast. Antibodies raised against tonoplast H+-
ATPase and H+-PPiase did not crossreact with 51-
kDa protein, although Al stress induced these enzymes
in the barley roots (Matsumoto et al., 1996; Taylor et
al., 1997).
E. Mucilage
The root apices of most plant species are covered by
mucilaginous substances that are excreted from root
volume). The meristem and cap region where Al
toxicity is dominant are coated with mucilage that
ranges in thickness from 50m to 1 mm. Mucilage
consists mainly of polysaccharides > 2 106 daltons.
Abundant sugars are glucose, galactose, and arabi-
nose. Uronic acids are smaller in amount but charac-teristic of the mucilage. Mucilage has various
protective functions against toxic metals in the soil
and has a high Al-binding capacity. Fifty percent of
the total Al of root apices of cowpea was associated
with mucilage (Horst et al., 1982). Al bound to muci-
lage of wheat roots accounted for $ 2535% of the Al
remaining after desorption by citric acid. The Al in
rhizosphere is bound to mucilage that blocks the
entry of Al into the root. When the mucilage was per-
iodically removed from the root tips of cowpea with a
brush, inhibition of root elongation was increased.
Apparently, binding of Al to mucilage is a mechanismof Al tolerance. A good correlation exists between
mucilage volume and Al tolerance. Organic acids
released into a mucilage droplet would diffuse slowly;
thus, the mucilage droplet would form a region of high
concentration of organic acids where Al is captured
before reaching the root surface.
However, a protective role of the mucilage against
Al injury is difficult to reconcile with the lack of evi-
dence that mucilage excretion affected by Al. On the
contrary, disappearance of mucilage is one of the first
visible symptoms of Al toxicity (Puthota et al., 1991).
The role of mucilage in the protection of roots against
Al toxicity depends on the amount of mucilage
excreted and how strongly Al bounds to mucilage.
Mucilage from maize roots is strongly bound to Al
but failed to prevent Al-induced inhibition of root
elongation (Li et al., 2000a). Approximately 50% of
the total Al of the root apices was located in the muci-
lage of cowpea, while only 922% of Al in maize root
was bound to mucilage. The binding is decreased by
the lower content of uronic acids (3%) in maize muci-
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lage as compared to 11.5% in cow pea mucilage (Li et
al., 2000a). It will be necessary to determine the Al-
binding sugar component in mucilage as well as total
amount of mucilage and kinetic data of synthesis and
excretion of mucilage in order to understand the role
of mucilage in Al resistance.
F. pH in the Rhizosphere
Solubility of Al depends strongly on pH. Thus, main-
tenance of a high solution pH may reduce the solubi-
lity and toxicity of Al. An increase in the pH of dilute
nutrient solution from 4.5 to 4.6 caused a 26% decline
in soluble Al concentration (Blamey et al., 1983). This
suggests that even a slight pH change can affect the
toxicity of Al as well as tolerance. However, measure-
ment of pH should be done carefully because the
change of pH near the root surface is important. For
this purpose, a vibrating microelectrode was used tomeasure pH at a radial distance of 20 and 50m
from the surface of the root tip of a wild-type and of
an Al-tolerant Arabidopsis (Degenhardt et al., 1998).
The Al-tolerant Arabidopsis mutant alr-104 showed a
clear increase of pH at the rhizosphere in the presence
of Al, but the wild type did not. Al exposure of alr-104
induced a twofold increase in net H influx localized at
the root tip. The increased flux raised the root surface
pH of alr-104 by 0.15 unit, suggesting that Al resis-
tance in alr-104 is mediated by pH change in the rhizo-
sphere. Difference in Al resistance between wild type
and alr-104 disappeared when roots were grown in pH-buffered medium. It is interesting that no difference in
root H fluxes between wild type and alr-104 was
detected in the absence of Al.
IV. BENEFICIAL EFFECT OF ALUMINUMON PLANT GROWTH
Plants that contain > 1000 ppm Al are called Al accu-
mulators. Among the 259 plant families, 37 Al accu-
mulator species were found and most of them are
arborescent cryptogams (Chenery and Sporne, 1976).
Al accumulators can grow in acid soils, and growth of
some of them is even promoted. Tea (Camellia sinensis)
may contain as much as 30,000 ppm Al in old leaves
but only 600 ppm in young leaves. The specific loca-
tions of Al in epidermis of old leaves and in the cell
lumen of bean and barley root was demonstrated by
the staining of Al with aluminon and by x-ray (EMX)
microanalysis (Waisel et al., 1970; Matsumoto et al.,
1976b). The secondary cell wall of epidermal cells of
old leaves is thicker and Al may have accumulated in
the cell wall during thickening. The formation of new
roots was greatly accelerated after 1 month of Al treat-
ment and thereafter the growth of tops was positively
affected (Matsumoto et al., 1976b). Tea is a sensitive
plant for phosphate nutrition and markedly inhibited
by the excess of phosphate. Konishi et al. (1985)
showed that maximum growth of tea occurred withcoexistence of Al with phosphate. The reduced growth
of tea at 0.8 mM phosphate was dramatically stimu-
lated by the presence of 1.6 mM Al with new root
formation. Al plays a regulatory role in the effective
absorption and utilization of phosphate. Another
strategy of tea plants against Al toxicity is binding of
most of Al to catechin, phenolics, and organic acids
(Nagata et al., 1992). The mechanism of Al tolerance is
generally carried out by internal detoxification or
excretion of chelators, but the mechanism of beneficial
effect of Al on the growth has not been clearly demon-strated.
V. CONCLUDING REMARKS
Inhibition of root elongation caused by Al toxicity is
one of the most deleterious factors for plant growth in
acid soils. Al3 concentrations as low as 1 mol at pH
4.55.0 inhibit root elongation within 1 h. Absorbed Al
is localized at the root apex, where it inhibits cell func-
tions. It is therefore important to know the effect of Al
on the processes of cell elongation and cell division atthe root apex.
There are several unsolved problems underlying the
mechanism of Al toxicity. The receptor of the Al signal
on root cell membrane and how the signal is trans-
mitted remain unknown. Does the signal work only
in the apoplast? If so, there must be a signal transduc-
tion system through the plasma membrane into the
symplast. Structural proteins like tubulin and actin
are candidates for participation in that system.
Another possibility is that Al itself is active in the sym-
plast. In this case, we must know the mechanism of Al
transport through the plasma membrane.
The role of organic acids, both intracellular and
extracellular, in the mechanism of Al tolerance has
been clarified markedly during the last decade. Al-tol-
erant plants accumulate less Al than sensitive ones, and
formation of chelaters reduces Al toxicity. The major
organic acids are citric, malic, and oxalic acids. Why
do different plant species excrete different organic acids
by the same Al signal? Is there any other Al-chelating
compounds of plant origin other than organic acids? Is
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the amount of excreted organic acids sufficient for Al
chelation in the rhizosphere in acid soil? (See also
Much progress has been made in the molecular
aspects of Al binding to oxalic acid and excretion
mechanism of malic acid. However, an important pro-
blem still to be solved is the regulatory mechanism of
the synthesis and excretion of organic acids upon theAl signal. The knowledge of the cell responses to the
short-term effects of Al is expected to help us to under-
stand the whole-plant responses and would lead to the
improvement of crop production under long-term
effects of Al.
ACKNOWLEDGMENT
The author wishes to thank Mrs. S. Rikiishi for her
careful preparation of the manuscript.
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