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Plant Physiol, November 2001, Vol. 127, pp. 817-831
Antioxidant Systems and
O2.
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ABSTRACT |
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The present work describes, for the first time, the changes that
take place in the leaf apoplastic antioxidant defenses in response to
NaCl stress in two pea (Pisum sativum) cultivars (cv Lincoln and cv Puget) showing different degrees of sensitivity to high
NaCl concentrations. The results showed that only superoxide dismutase,
and probably dehydroascorbate reductase (DHAR), were present in the
leaf apoplastic space, whereas ascorbate (ASC) peroxidase,
monodehydroascorbate reductase (MDHAR), and glutathione (GSH) reductase
(GR) seemed to be absent. Both ASC and GSH were detected in the leaf
apoplastic space and although their absolute levels did not change in
response to salt stress, the ASC/dehydroascorbate and GSH to GSH
oxidized form ratios decreased progressively with the severity of the
stress. Apoplastic superoxide dismutase activity was induced in
NaCl-treated pea cv Puget but decreased in NaCl-treated pea cv Lincoln.
An increase in DHAR and GR and a decrease in ASC peroxidase, MDHAR,
ASC, and GSH levels was observed in the symplast from NaCl-treated pea
cv Lincoln, whereas in pea cv Puget an increase in DHAR, GR, and MDHAR
occurred. The results suggest a strong interaction between both cell
compartments in the control of the apoplastic ASC content in pea
leaves. However, this anti-oxidative response does not seem to be
sufficient to remove the harmful effects of high salinity. This finding
is more evident in pea cv Lincoln, which is characterized by a greater
inhibition of the growth response and by a higher rise in the
apoplastic hydrogen peroxide content, O2.
production and thiobarbituric acid-reactive substances, and CO protein
levels. This NaCl-induced oxidative stress in the apoplasts might be
related to the appearance of highly localized
O2.
/H2O2-induced
necrotic lesions in the minor veins in NaCl-treated pea plants. It is
possible that both the different anti-oxidative capacity and the
NaCl-induced response in the apoplast and in the symplast from pea cv
Puget in comparison with pea cv Lincoln contributes to a better
protection of pea cv Puget against salt stress.
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INTRODUCTION |
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NaCl stress is a major factor
limiting crop production because it affects almost all plant functions
(Bohnert and Jensen, 1996
). Therefore, it is important to understand
how plants respond and adapt to such stress. Adaptation of the plant
cells to high salinity involves osmotic adjustment and the
compartmentation of toxic ions, whereas an increasing body of evidence
suggests that high salinity also induces oxidative stress
(Hernández et al., 1993
, 1995
, 1999
; Gosset et al., 1996
;
Gómez et al., 1999
; Savouré et al., 1999
). Therefore,
antioxidant resistance mechanisms may provide a strategy to enhance
salt tolerance, and processes underlying antioxidant responses to salt
stress must be clearly understood. In previous studies, we have
suggested a pivotal role for subcellular compartmentation in
antioxidant defense mechanisms under stress conditions, including
senescence and NaCl stress (Jiménez et al., 1997
, 1998a
; del
Río et al., 1998
; Gómez et al., 1999
).
In pea (Pisum sativum) plants, it has been demonstrated that
the metabolism of chloroplasts and mitochondria under NaCl stress favored the formation of O2.
and H2O2 in two pea
cultivars differing in NaCl sensitivity (Hernández et al., 1993
,
1995
). When the effect of salt stress on the antioxidant defenses was
examined at the transcript levels of mitochondrial, chloroplast, and
cytosolic enzymes, an increase in all the components of the ascorbate
(ASC)-glutathione (GSH) cycle and superoxide dismutase (SOD) isozymes
was only found in tolerant pea plants (Gómez et al., 1999
;
Hernández et al., 2000
). Transcript levels for mitochondrial
Mn-SOD, chloroplastic CuZn-SOD and phospholipid hydroperoxide GSH peroxidase, and cytosolic GSH
reductase (GR) and ASC peroxidase (APX) were strongly induced in
the salt-tolerant variety but not in the salt-sensitive one, suggesting
that the induction of antioxidant defenses is one component of the
tolerance mechanisms of peas to long-term salt treatment
(Hernández et al., 2000
).
The effects of both biotic and abiotic stress on the antioxidant
systems of the apoplastic space have been studied by some authors, and
results suggest that this compartment could be important in the plant
cell response to SO2, O3,
and pathogens (Dietz, 1996
; Luwe, 1996
; Vanacker et al., 1998a
, 1998b
).
Likewise, it is known that the above-described elicitors are capable of
inducing the synthesis of activated oxygen species (AOS) in the
apoplast of plant cells and also modulate the level of cellular
antioxidants as well as the levels of apoplastic antioxidant enzymes
(Luwe, 1996
; Ranieri et al., 1996
; Blinda et al., 1997
;
Thordal-Christensen et al., 1997
; Schraudner et al., 1998
;
Vanacker et al., 1998a
, 1998b
; Piqueras et al., 1999
; Hernández
et al., 2001
). However, little is known about the capacity of salt to
induce the synthesis of AOS in the apoplast and, in this case, the role
played by apoplastic antioxidants. This information is important
because in plant cells subject to salt stress, initial events most
likely occur externally in the apoplasm-cell membrane space.
Nevertheless, relatively little information is available
regarding the presence of the antioxidant enzymes and
low-Mr antioxidants, such as ASC and GSH,
in the apoplast of plant tissues (Vanacker et al., 1998a
), and
the results found are often contradictory. Thus, although previous
studies have failed to detect the antioxidant enzymes of the ASC-GSH
cycle in the apoplast (Castillo and Greppin, 1988
; Polle et al., 1990
;
Luwe, 1996
) Vanacker et al. (1998a
, 1998b
) recently described the
presence not only of SOD activity, but also APX, monodehydroascorbate
reductase (MDHAR), dehydroascorbate (DHA) reductase (DHAR), GR, and
catalase in the apoplast from both barley (Hordeum
vulgare) and oat (Avena sativa) leaves. In regard to
the antioxidants ASC and GSH, it should be pointed out that although
both ASC and DHA are apparently present in high concentrations in the
leaf apoplast (Polle et al., 1990
; Luwe, 1996
; Ranieri et al., 1996
;
Vanacker et al., 1998a
, 1998b
), the presence of GSH is still uncertain,
and little or no GSH has been found in the apoplast of plant cells
(Luwe, 1996
; Vanacker et al., 1998a
, 1998b
).
In this work, the presence of SOD and of the enzymes of the ASC-GSH
cycle (APX, MDHAR, GR, and DHAR), as well as the ASC and GSH contents,
were studied in the leaf apoplastic space of two pea cultivars, one
sensitive (cv Lincoln) and the other relatively tolerant (cv Puget) to
70 mM NaCl. This study was carried out to characterize the
antioxidant capacity in this cell compartment and also to observe its
behavior in the face of possible oxidative perturbation induced by an
NaCl stress situation. In both pea cultivars, salt stress induces
oxidative effects in the apoplasts, although such effects are lower in
the relatively NaCl-tolerant pea (cv Puget) cultivar than in the
NaCl-sensitive (cv Lincoln) plants. Oxidative damage was shown by the
appearance under high NaCl stress of highly localized
O2.
/H2O2-induced
necrotic lesions in minor veins, which resemble the microburst observed
by other authors in response to pathogenic (biotic) stress situations.
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RESULTS |
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The growth of pea cv Lincoln plants, estimated as shoot fresh
weight (Fig. 1A) and shoot dry weight
(Fig. 1B), was not affected by 50 mM NaCl in the nutrient
medium, but was reduced by about 30% and 50% in the presence of 70 and 90 mM NaCl, respectively, demonstrating that this pea
cultivar is tolerant to 50 mM NaCl but sensitive to higher
NaCl concentrations. In a previous study, the growth response of
pea cv Puget, also estimated as shoot fresh and dry weight, among
others parameters, seemed to not be significantly reduced by 70 and 90 mM NaCl (Hernández et al., 1999
; Fig. 1, C and D),
indicating that this pea cultivar is relatively NaCl tolerant.
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In pea cv Lincoln, the H2O2 content of the intercellular washing fluid (IWF) from NaCl-treated plants increased 4.8-, 10.0-, and 11.6-fold in plants treated with 50, 70, and 90 mM NaCl, respectively (Fig. 2A). The concentration of H2O2 in the apoplastic fluid ranged from 0.06 µM in control leaves to 0.70 µM in 90 mM NaCl-stressed pea leaves. The rise in H2O2 in 70 and 90 mM NaCl-treated plants was matched by an increase in lipid peroxidation (Fig. 2B), and protein oxidation at the higher NaCl concentration (Fig. 2C). In pea cv Puget plants, the H2O2 content in the IWF also increased with the severity of the stress but was limited to only 2.7-fold at 90 mM NaCl. Thus, the concentration of H2O2 in the apoplastic fluid ranged from 0.06 µM in control leaves to 0.20 µM in 90 mM NaCl-stressed plants (Fig. 2D). In pea cv Puget plants, 90 mM NaCl produced an increase in lipid peroxidation and protein oxidation (Fig. 2, E and F), although not so high as in pea cv Lincoln.
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The treatment of pea cv Lincoln plants with 90 mM NaCl also
produced the appearance of necrotic leaf lesions localized initially on
minor veins. These necrotic lesions can be easily monitored during the
first stages of injury by the bleaching of chlorophylls (Fig.
3A, arrows). As the lesions advance, they
turn brown and their size becomes visible to the naked eye. No necrotic
lesions were observed in control plants at any time of the culture
period. When these salt-induced necrotic lesions (SINLs) of minor veins were stained with Nitroblue tetratolium (NBT) during the first stages
of development, a blue/red wine staining appeared on the cell walls of
mesophyll cells (Fig. 3B). This staining was due to the production of
O2.
because it was totally
suppressed by SOD (Fig. 3C, arrows), and by 10 mM
MnCl2, a highly effective dismutating catalyst
agent of O2.
(Fig.
4).
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When O2.
production, as
monitored by NBT, was followed with the degree of severity (judging
from increased lesion size) of the SINLs (Fig.
5, A-C) in pea leaves, the formation of
an O2.
-generating front was
observed on the outer edge of the necrotic lesion (Fig. 5C, arrows).
This O2.
-generating front was
clearly distinguishable from the strictly local production of
O2.
, which takes place during
the first stages of lesion development (Fig. 5A). These results suggest
that the SINLs advance as the O2.
production front advances,
suggesting a key role for O2.
in the development of these SINLs.
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When stained with the diaminebenzydine (DAB) reagent to locate
H2O2, the SINLs also showed
a red-brown staining localized on the cell walls of mesophyll cells
(Fig. 6A), which diffused rapidly through
the minor veins of the leaf (Fig. 6B, arrows), probably due to the
greater half-life time of
H2O2 compared with O2.
. This staining seemed to
be due to H2O2 because it
was totally suppressed by 10 mM ascorbic acid (Fig. 6C,
arrows). DAB-stainable AOS production was also observed in the
relatively salt-tolerant cultivar (pea cv Puget), where the lesions
were somewhat smaller in size (compare Fig. 6, D with E).
|
The quantification of SOD activity in the apoplast of control and
salt-stressed pea plants took into account corrections for cytosolic
and chloroplastic protein contamination of the IWF during the
infiltration procedure. In this way, the activity of the cytosolic and
chloroplastic triose phosphate isomerase (TPI) was analyzed. The
results showed that contamination was always less than 1.0% in control
plants. However, the percentage of contamination increased with the
severity of salt treatment, probably due to cellular injury, reaching
about 1.54% in pea cv Lincoln and 2.38% in pea cv Puget plants
treated with 90 mM NaCl (Table
I). According to the results obtained
with the inhibitors, H2O2
and KCN, CuZn-SOD activity seems to be present in the apoplastic space
of control pea cv Lincoln (Fig. 7) and
control pea cv Puget leaves (results not shown). This CuZn-SOD could
not be clearly distinguished from the major cytosolic CuZn-SOD I
present in pea leaves using native PAGE (Fig. 7) or isoelectrofocusing
at different pH ranges (results not shown). Thus, the detection of
apoplastic CuZn-SOD activity was carried out taking into account the
different isozyme patterns shown by the symplastic and apoplastic
fractions (Fig. 7). In leaf crude extract from pea cv Lincoln plants,
three different SOD activity bands were detected, an Mn-containing SOD
and two CuZn-containing SOD (named I and II in order of increased
mobility), representing 14% to 15%, 34% to 36%, and 48% to 50%,
respectively (Fig. 7). In pea plants, Mn-SOD is localized in
mitochondria and peroxisomes, CuZn-SOD I in the cytosol, and CuZn-SOD
II in chloroplasts (Hernández et al., 1999
). In the apoplastic
fraction, we detected the same number of SOD isozymes as in crude leaf
extracts, but in the apoplast, mitochondrial and peroxisomal Mn-SOD and
chloroplastic CuZn-SOD II only accounted for 4% to 5% and 33% to
35%, respectively, whereas cytosolic Cu,Zn-SOD represented 60% to
62% of the total SOD activity found in this compartment. By
isoelectrofocusing of the apoplastic fraction, the percentage of
CuZn-SOD I increased from 53% to 55% and that of CuZn-SOD II
decreased to 45% from 47% in relation to the values in the symplastic
fraction (data not shown).
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In control pea cv Lincoln leaves, apoplastic CuZn-SOD only represents 1% of total leaf SOD activity, this percentage being lower in pea cv Puget plants (0.35%). This apoplastic CuZn-SOD activity was not affected in pea plants of either cultivar treated with 50 and 70 mM NaCl but decreased significantly, to 54%, in pea cv Lincoln plants subjected to 90 mM NaCl (Fig. 8A). In contrast, a 90-mM NaCl treatment brought about a significant increase, by up to 60%, in the activity of apoplastic CuZn-SOD in pea cv Puget plants (Fig. 8B).
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Following corrections for cytosolic and chloroplastic protein contamination, only DHAR activity was detected in the apoplastic space of both pea cultivars, where it represented 0.26% and 1.78% of the total leaf DHAR activity in pea cv Lincoln and pea cv Puget, respectively (Table II). p-CMPS-sensitive APX, p-CMPS-insensitive APX, MDHAR, and GR activities were apparently not located in the leaf apoplast of either cultivar because the values corresponding to these enzymes in the apoplast were possibly due to cytosolic and/or chloroplastic contaminations (Table II). Similar results were found in NaCl-treated plants, although in these cases, DHAR activity was mainly, and probably exclusively, due to chloroplastic and/or cytosolic contamination (Table II).
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The effect of salt stress on the "symplastic" enzymes was studied using the leaf residue resulting from the IWF extraction (Table II). DHAR activity increased in the "symplast" fraction of pea cv Lincoln plants treated with 70 and 90 mM NaCl (1.44- and 1.61-fold, respectively). GR activity showed a rise of about 30% at these NaCl concentrations, and MDHAR and p-CMPS-sensitive APX decreased in all the NaCl-treated plants (Table II). No effect of salinity on either "symplastic" p-CMPS-insensitive APX or SOD activity was observed (Table II). In pea cv Puget plants, DHAR and GR activity gradually and significantly increased with the severity of the stress although, unlike in pea cv Lincoln plants, MDHAR remained constant at 70 mM NaCl but was significantly induced at 90 mM NaCl, whereas p-CMPS-sensitive APX activity only fell at this NaCl concentration. No effect of NaCl on "symplastic" SOD activity was observed (Table II).
In control pea cv Lincoln leaves, the ASC content of the apoplast (0.12 mM) represented about 6% of the total ASC, whereas the apoplastic DHA content (3.6 µM) represented 2% of the total oxidized ASC present in leaves. In pea cv Puget plants, the ASC content of the apoplast (0.21 mM) was about 2-fold higher than in pea cv Lincoln, and represented by up to 9.5% of the total leaf ASC. In a similar manner, the apoplastic DHA content (7.1 µM) was higher in pea cv Puget than in pea cv Lincoln, representing 5.2% of the total leaf DHA. In neither pea cultivar did the ASC content change significantly in the leaf apoplast from NaCl-stressed plants (Fig. 9, A and C). However, DHA was observed to accumulate in the leaf apoplast of 90 mM NaCl-treated pea plants, particularly in the pea cv Lincoln (2.6-fold increase, from 3.6 to 9.1 µM; Fig. 9A) compared with the 1.5-fold increase (from 7.1 to 11.5 µM) seen in pea cv Puget (Fig. 9C). In both cultivars, the ASC to DHA ratio gradually decreased with the severity of the stress.
|
As a result of the increasing salt stress, the ASC pool decreased progressively in the "symplastic" fraction from pea cv Lincoln leaves (by up to 52% in plants treated with the higher NaCl concentration; Fig. 9B). However, in the same conditions, the "symplastic" ASC content from pea cv Puget plants decreased by up to 20% (Fig. 9D). In both cultivars, the "symplastic" DHA content was not affected by treatment with 50 mM NaCl, although its content decreased progressively in plants treated with 70 and 90 mM NaCl (Fig. 9, B and D). As a result of these changes, the symplastic ASC to DHA ratio increased with the severity of the stress in both cultivars.
The apoplastic GSH content of pea cv Lincoln leaves represented about 5.6% of the total GSH pool in leaves, a percentage similar to that observed for ASC. The percentage of GSH in the leaf apoplast increased by up to 8.7% of the total GSH present in the leaf with the 50 mM NaCl treatment, but showed no statistical changes at higher salt concentration (Fig. 10A). The percentage for glutathione oxidized form (GSSG) in the leaf apoplast from pea cv Lincoln plants was about 18%, and only increased significantly (2.55-fold) in the leaf apoplast of pea plants treated with 90 mM NaCl (Fig. 10A). A higher percentage of GSH was found in the apoplast of pea cv Puget plants, ranging from 16% to 22%, and the values were nearly three times higher than in pea cv Lincoln (Fig. 10C). The percentage of GSSG in the apoplast of control pea cv Puget plants was lower (only 5.2%) than in pea cv Lincoln. However, at 70 and 90 mM NaCl, similar percentages were found in both cultivars, and a significant increase of GSSG was found in the apoplast of pea cv Puget plants treated with these salt levels (Fig. 10C).
|
The GSH content decreased significantly in the "symplast" from both pea cultivars only in plants treated with 90 mM NaCl (Fig. 10, B and D). However, an increase in the GSSG content was invariably observed in the "symplast" from pea cv Lincoln plants subjected to salt stress (as much as 2.52-fold at 90 mM NaCl; Fig. 10B), so that the "symplast" GSH to GSSG ratio decreased in NaCl-treated plant of this cultivar. However, no significant GSSG accumulation was observed in the symplast from pea cv Puget plants (Fig. 10D) and the GSH to GSSG ratio slightly decreased.
When the effect of salt stress on apoplastic p-CMPS-insensitive (class
III) peroxidases was studied, the results showed that such activity in
pea cv Lincoln plants, measured with both non-physiological (4-methoxy-
-naphthol and 3,3',5,5'-tetra methylbenzidine) and physiological (coniferyl alcohol) substrates, increased in response to
salt stress, although these changes were not statistically significant (Table III). The highest
stimulation was attained with 70- and 90-mM NaCl treatments
when 4-MN and coniferyl alcohol, respectively, were used as substrates.
Similar results were obtained in the relatively salt-tolerant pea
cultivar (data not shown). Isoenzyme patterns of apoplastic class III
peroxidase only showed minor (nonsignificant) changes in response to
salt treatment, and the effect seemed to be general for all the
isoenzymes (results not shown).
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DISCUSSION |
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A comparison of the growth response to salt stress shows that pea
cv Lincoln is tolerant to 50 mM NaCl, although it is more sensitive to higher NaCl concentrations than pea cv Puget. The latter
was previously designated as moderately tolerant to NaCl stress, when
its growth response was compared with that reported for other
leguminous plants, including different pea cultivars (Hernández
et al., 1995
, 1999
; Gómez et al., 1999
).
Evidence for the effects of salt stress-inducing changes in plant
metabolism is well documented (Greenway and Munns, 1980
). Salt stress,
in addition to the known components of osmotic stress and ion toxicity,
is also manifested as an oxidative stress, and all of these contribute
to its deleterious effect (Gueta-Dahan et al., 1997
). However, ion
content and salt tolerance are not often correlated, and several
studies indicate that acquisition of salt tolerance may also be a
consequence of improving resistance to oxidative stress
(Hernández et al., 1993
, 1995
, 1999
; Gosset et al., 1996
; Streb
and Feierabend, 1996
; Gueta-Dahan et al., 1997
; Gómez et
al., 1999
).
Very few enzymes and metabolites have been shown unequivocally to be
either absent or present in the apoplast (Dietz, 1996
). Moreover, unavoidable contamination by cytosolic and chloroplastic components occurs. In this work, TPI was used both as a cytosolic and a
chloroplastic marker to determine the degree of contamination of the
apoplastic space by components originating in the symplast of plant
cells because SODs and the enzymes of the ASC-GSH cycle are mainly
accumulated in those subcellular compartments (Jiménez et al.,
1997
, 1998a
; Ogawa et al., 1997
; Foyer and Mullineaux, 1998
;
Gómez et al., 1999
; Hernández et al., 2000
).
In pea apoplast, values found for SOD activity agree with data for
Scots pine (Pinus sylvestris) needles and oat and
barley leaves (0.1%-2.5% of total activity; Streller and Winsgle,
1994
; Vanacker et al., 1998a
, 1998b
). In agreement with reports
for apoplastic CuZn-SOD from spinach leaves (Ogawa et al., 1996
, 1997
), the apoplastic CuZn-SOD isozyme detected in both pea cultivars here
seems to be indistinguishable from the main cytosolic CuZn-SOD, at
least under our experimental conditions.
The absence of APX activity in the apoplast of both pea cultivars
agrees with what has been also reported for different plants (Polle et
al., 1990
; Durán Carril and Rodriguez-Bujan, 1999
). Our
results differ from those reported by Vanacker et al. (1998)
, who
described the presence not only of SOD and APX activity in the apoplast
of both barley and oat leaves, but also of MDHAR, DHAR, GR, and
catalase. In our pea cultivars, similar percentages for these enzymes
were observed in the apoplast (Table II). However, these activities
were apparently due to cytosolic and/or chloroplastic contaminations,
which ranged from 0.86% to 1.03% in control leaves to 1.54% to
2.38% in 90 mM NaCl-treated pea plants (cv Lincoln and cv
Puget, respectively).
It is necessary to point out that the presence of DHAR in the apoplast
of control pea leaves is still uncertain in both cultivars, if the
total chlorophyll content of the apoplastic solution was considered as
a symplastic marker instead of TPI activity. This fact is also
supported by the absence of GR activity in the apoplast. No DHAR
activity could be measured in the apoplastic space of beech
(Fagus sylvatica) leaves (Luwe, 1996
) and, recently,
Morell et al. (1997)
have reported that a certain pseudo-DHAR activity found in plants may be due to side reactions of proteins containing redox-active di-Cys sites. However, Foyer and Mullineaux (1998)
expressed several consistent arguments in favor of the presence of DHA
and DHAR activity in plant tissues. Moreover, the presence of a plasma
membrane-associated MDHAR, which may play a role in the reduction of
ASC in both cytosol and apoplast, has been described (Navas and
Gómez-Díaz, 1995
; Bérczi and Möller,
1998
). All these results suggest that the presence of a "DHAR
enzyme" in the apoplast fraction of pea leaves should be regarded
with caution.
The ASC levels in the apoplast of spinach (0.65 mM), barley
(0.016 mM), and oat leaves (0.01 mM; Takahama
and Okini, 1992
; Vanacker et al., 1998a
, 1998b
) agree well with
the ASC concentration present in the pea leaf apoplast, which ranged
from 0.12 to 0.22 mM. A different picture exists regarding
GSH because little or no GSH has been detected in the apoplast of
certain plant cells. This has been found in the apoplast from
Picea abies needles (Polle et al., 1990
) and in the apoplast
of barley leaves (Vanacker et al., 1998b
), where its concentration
ranged from 6 to 6.5 µM. GSH concentration in
pea leaf apoplast was lower and ranged from 0.8 to 1.2 µM for pea cv Lincoln and from 2.0 to 2.4 µM from pea cv Puget.
In response to NaCl stress conditions, the appearance of SINLs in the
minor veins of 90 mM NaCl-treated plants supports the establishment of an oxidative stress situation in the apoplasts of both
pea cultivars. The NaCl-induced oxidative stress situation is observed
as highly localized areas of AOS
(O2.
and
H2O2) production in minor
veins in both pea cultivars and is also manifested by increases in
lipid peroxidation, H2O2
content, and protein oxidation. However, some differences between both pea cultivars were found because all the above oxidative effects were
less pronounced in pea cv Puget (Fig. 6D) than in pea cv Lincoln (Fig.
6E) in 90 mM NaCl stress conditions, as reflected by the
smaller necrotic lesions in pea cv Puget plants.
However, these areas of
H2O2 production in pea
leaves, as seen histochemically, never exceeded 0.25% of the total
leaf area in 90 mM NaCl-stressed plants. Based on an
H2O2 concentration of 0.70 µM in the whole-leaf apoplast of 90 mM
NaCl-stressed pea cv Lincoln plants, this means that the local
H2O2 concentration in the
area of the SINL would reach 250 to 300 µM. This last
value for the H2O2 content
of SINLs fits in well with the fact that, although DAB can detect
H2O2 in leaves at levels as
low as 10 µM, strong color only develops with
concentrations above 100 µM (Thordal-Christensen
et al., 1997
).
These SINLs emerge from periveinal zones with a capacity for sustaining
net O2.
and
H2O2 production in the
first stages of development. These stained areas were sensitive to ASC,
and therefore were indicative for
H2O2 accumulation. The
generation of necrotic lesions under NaCl stress resembles the leaf
"microbursts" observed by other authors in response to pathogenic
stress situations where
H2O2 is accumulated
(Alvarez et al., 1998
; Orozco-Cardenas and Ryan, 1999
). AOS
accumulation, cell death, and lesion in the vicinity of leaf veins have
been observed in ozone-treated tobacco leaves (Schraudner et al.,
1998
). In pea plants, the fact that the lesions generated under NaCl
stress are associated with high levels of O2.
and
H2O2 production provides
strong evidence that these lesions may be part of an active
hypersensitive-like response. These observations may be interpreted as
indicating that in pea cv Lincoln the down-regulated apoplastic SOD
activity together with the lower constitutive levels of reduced ASC and
GSH, compared with that found in pea cv Puget, could contribute to
allowing O2.
and
H2O2 to destroy plant cells
to a greater extent than in pea cv Puget, where the NaCl-induced
lesions were less extensive.
The induction of apoplastic SOD in pea cv Puget might be responsible for increasing the apoplastic H2O2 content, although this metabolite, among others, could be directly scavenged by ASC, whose levels were 2-fold higher in this cultivar than in pea cv Lincoln.
It is important to note that the up-regulation of antioxidant enzymes,
rather than the constitutive apoplastic level of SOD, among other
factors, seems to be important in the tolerance of pea cv Puget to salt
stress. This relationship was previously observed in other pea
cultivars (Hernández et al., 1993
, 1995
, 2000
; Gómez et
al., 1999
), and it was reported in different plants, including the
pst1 Arabidopsis mutant (Tsugane et al., 1999
). In addition,
it has been reported that overexpression of SOD confers salt tolerance
to rice (Oryza sativa) plants (Tanaka et al., 1999
), further confirming that O2.
and derived AOS are involved in salt-induced damages. Leaf lesions under NaCl treatment were detected in mesophyll cells. A similar pattern of AOS accumulation was reported in ozone-treated plants (Schraudner et al., 1998
), but a different pattern was observed in
epidermal cells of barley following pathogen infection
(Thordal-Christensen et al., 1997
) and in tobacco following
elicitor treatment (Allan and Fluhr, 1997
).
Extracellularly secreted enzymes such as peroxidase are also know to
catalyze the production of O2.
(Kawano and Muto, 2000
). However, no significant changes in pea apoplastic p-CMPS-insensitive peroxidase were brought about by NaCl
stress. On the other hand, a membrane NAD(P)H oxidase has been proposed
as being responsible for the generation of AOS
(O2.
and subsequent
H2O2) in response to
pathogens (Levine et al., 1994
). There have been numerous reports
indicating the production and involvement of AOS in cation-induced
injuries (Cakmak, 2000
; Quartacci et al., 2001
). It was
proposed that, analogous to the mammalian enzyme, it is likely that
NADPH oxidase can be activated by cations (Cross et al., 1999
). This
enzyme, together with oxalate oxidase in the apoplast, could be the
enzymatic source participating in AOS accumulation during NaCl stress,
similar to that suggested under ozone stress (Schraudner et al., 1998
).
Further studies would determine the contribution of these enzymes to
NaCl-induced O2.
generation.
In salt-treated pea plants, uptake of the oxidized ASC through the
plasma membrane may represent an important step in the regeneration of
apoplastic ASC. Such ASC regeneration has been described by Horemans et
al. (1996
, 1997
), who demonstrated the existence of a carrier-mediated
ASC/DHA transport system that preferentially translocates DHA from the
apoplast to the cytosol and that probably exists to reduce this
molecule in this cell compartment (Castillo and Greppin, 1988
; Luwe et
al., 1993
; Horemans et al., 1997
). This mechanism could be occurring in
both pea cultivars, although its efficacy seems to be rather low in
NaCl-stressed plants, particularly in pea cv Lincoln. Thus, in both
cultivars, the lack of variation in total apoplastic ASC under NaCl
stress was accompanied by a decrease in both the apoplastic ASC to DHA ratio and the ASC redox state, in both cases mainly due to the increase
in the apoplastic DHA content. However, all these changes were less
pronounced in pea cv Puget that in pea cv Lincoln, in which the
increase in apoplastic DHA content was much higher under NaCl stress.
Changes in the redox balance in the apoplastic antioxidant system have
also been reported in response to ozone (Schraudner et al., 1998
),
pathogens (Thordal-Christensen et al., 1997
), and heavy metals
(Piqueras et al., 1999
).
This suggested mechanism for apoplastic regeneration fits with the
induction found in the symplastic DHAR and GR activities under NaCl
stress, showing that "symplastic" ASC is regenerated using the GSH
pool, although in pea cv Puget its regeneration could also involve
MDHAR activity. This is in agreement with reports for other pea
cultivars (Morán et al., 1994
; Hernández et al., 2000
).
Thus, it seems that neither MDHAR nor DHAR limited the ASC content of
the symplast or affected its reduction state, both of which seem to be
determined by its rate of synthesis and degradation and/or its
transport to other cell compartments. Similar to our findings in other
pea cultivars (Hernández et al., 2000
), it should be noted that
symplastic DHA accumulation does not occur in either pea cv Lincoln or
pea cv Puget.
GSH oxidation seems to occur at a higher rate in the symplast of pea cv
Lincoln under NaCl stress because in such conditions a progressive
increase in the symplastic GSSG content was observed. This fact could
be related to a higher degree of induction of DHAR than of GR in the
symplast, especially at 90 mM NaCl. Like ASC, constitutive
apoplastic GSH content was much more elevated in pea cv Puget than in
pea cv Lincoln plants, and showed no significant variations at higher
salt concentrations, at which a decrease in both the GSH to GSSG ratio
and the GSH redox state in this compartment occurred. The presence of
GSSG in the apoplast may be the result of the oxidizing conditions
existing in the cell wall, and of the interaction between GSH and the
disulfides from membrane and apoplastic enzymes. This could explain why
the GSSG level was higher in the apoplast than in the symplast. GSH
synthesis seems to take place in the cytosol and in chloroplasts
(Noctor et al., 1998
), but the presence of a GSH transporter at the
plasma membrane has been described (Jamaï et al., 1996
).
Therefore, this GSH transporter would retrieve GSSG for its reduction
and recycling to the cytoplasm (Jamaï et al., 1996
) and it
seems to be similar to the previously described ASC/DHA transporter (Horemans et al., 1996
).
In conclusion, salt stress produced an
O2.
- and
H2O2-mediated oxidative
stress in the apoplast, which brought about visible NaCl injuries. A
dual function of AOS, including
O2.
and
H2O2, in
exacerbating damage and signaling the activation of defense responses has been described, firstly in
pathogenesis (Dat et al., 2000
), and more recently during plant
responses to several abiotic stresses, including salt stress
(Gueta-Dahan et al., 1997
; Meneguzzo et al., 1999
). Our results are in
agreement with those previously reported, in which a lethal level of
AOS damages the cell, whereas a moderate level of AOS enhances the adaptation to salt stress (Hernández et al., 1995
; Gueta-Dahan et
al., 1997
). We suggest that NaCl is an abiotic elicitor of phytopathological and anti-oxidative defenses. In fact, together with
AOS production and cell death, overlap in induced gene expression after
pathogen and NaCl exposure has been observed (Knight et al., 1997
;
Delumeau et al., 2000
). As has been reported under ozone stress, it
seems that parts of the mechanisms involved in plant pathogen responses
are also induced by NaCl stress, although in this case the appearance
of necrotic leaf lesions is associated with sensitivity.
| |
MATERIALS AND METHODS |
|---|
|
|
|---|
Plant Material and Growth Conditions
Seeds of pea (Pisum sativum L. cv Lincoln and cv
Puget) plants supplied by Arnedo (Navarra, Spain) and Sharpes
International Seeds Ltd. (Sleaford, UK), respectively, were surface
sterilized and germinated in vermiculite with 0.5 mM
CaSO4 for 1 week. Seedlings were grown in pots containing
aerated nutrient solution in a growth chamber (ASL, Madrid) under
optimal conditions for 7 d, as described by Hernández et al.
(1999)
. After that time, plants were grown in a similar medium
supplemented by different NaCl concentrations (0, 50, 70, and 90 mM) for 14 d.
Extraction of the IWF
For the recovery of the IWF, 20 g of pea leaves was soaked in deionized water, and subsequently vacuum infiltrated for 3 min at 1.0 KPa and 4°C with 50 mM K-phosphate buffer (pH 6.5) containing 0.2 M KCl and 0.1 mM CaCl2. For APX activity, 5 mM sodium ASC was added. Leaves were then quickly dried and centrifuged at 1,000g for 5 min at 4°C in a 25-mL syringe barrel placed in a centrifuge tube.
To assay enzymatic activities and carbonyl-protein content, the IWF fraction was concentrated about 10-fold using Centripep 10 tubes (Amicon, Bedford, MA) and prepurified by chromatography on Sephadex G-50 MPD10 columns (Pharmacia Biotech AB, Uppsala) equilibrated with 50 mM K-phosphate buffer (pH 6.5) with or without 5 mM sodium ASC. To determine H2O2 and lipid peroxidation, the IWF fraction obtained after centrifugation at 1,000g was used directly. For ASC and GSH analysis, leaves were infiltrated with cold metaphosphoric acid (2%, w/v), containing 0.1 mM bathophenanthroline-disulfonic acid and centrifuged as above. Apoplastic concentrations for H2O2 and other apoplastic metabolites are given without correction for any dilution due to infiltration of the air spaces.
Contamination by cytoplasmic and chloroplastic constituents was
assessed by measuring the levels of TPI (Feierabend, 1975
) and
chlorophylls (Arnon, 1949
). Glc-6-phosphate dehydrogenase was not used
as cytosolic marker because it has been reported that only 10% of this
enzyme is present in the cytosol fraction from pea plants (Corpas et
al., 1998
).
Leaf Enzyme Extraction
All operations were performed at 4°C. Leaf residues (2 g), which resulted from IWF extraction, were homogenized with a mortar and pestle in 4 mL of ice-cold 50 mM K-phosphate buffer, pH 7.8, 0.1 mM EDTA containing 5 mM Cys, 1% (w/v) polyvinyl pyrrolidone, 0.1 mM phenylmethylsulfonic fluoride, and 0.2% (v/v) Triton X-100. For APX activity, 20 mM sodium ASC was added. The "symplastic" homogenate was centrifuged at 14,000g for 20 min and the supernatant fraction was filtered through Sephadex G-50 PD10 columns (Pharmacia Biotech AB), equilibrated with the same buffer used for the homogenization, with or without 5 mM sodium ASC.
Determination of H2O2, Lipid Peroxidation, and Protein Oxidation
The H2O2 concentration in IWF was
determined immediately after isolation by a peroxidase-coupled assay
using 4-aminoantipyrine and phenol as donor substrates (Frew et al.,
1983
). The carbonyl content in oxidatively modified proteins was
quantified using the 2,4-dinitrophenylhydrazone assay procedure
(Levine et al., 1990
). The extent of lipid peroxidation in apoplastic
fluid was estimated by determining the concentration of substances
reacting to thiobarbituric acid-reactive substances (Buege and Aust,
1978
).
Enzymatic Activities of the ASC-GSH Cycle
APX, DHAR, MDHAR, and GR activities were assayed according to
previously published protocols, as described by Jiménez et al.
(1997)
. Enzyme activities were corrected for nonenzymatic rates and for
interfering oxidations (Jiménez et al., 1997
). For APX, the
oxidation rate of ASC was estimated between 1 and 60 s after
starting the reaction by the addition of H2O2.
Correction was made for the low nonenzymatic oxidation of ASC by
H2O2. APX was measured in the presence and
absence of the specific inhibitor pCMPS (0.5 mM).
pCMPS-sensitive APX activity was considered as being due to class I APX
(EC 1.11.1.11), whereas pCMPS-insensitive APX activity was considered
as due to class APX (EC 1.11.1.7), i.e. APX activity due to
substrate-unspecific (guaiacol) class III peroxidases
(Jiménez et al., 1998b
). To determine MDHAR activity, monodehydroascorbate was generated by the ASC/ASC oxidase system. The
rate of monodehydroascorbate-independent NADH oxidation (without ASC
and ASC oxidase) was subtracted from the initial
monodehydroascorbate-dependent NADH oxidation rate (with ASC and ASC
oxidase). For DHAR activity, the reaction rate was corrected for the
nonenzymatic reduction of DHA by GSH. A factor of 0.98 was considered
to account for the small contribution to the absorbance by GSSG. Values
due to GR activity were corrected for the small, nonenzymatic oxidation of NADPH by GSSG (Jiménez et al., 1997
). The values of the
ASC-GSH cycle enzymes determined in the apoplast fractions were
corrected by the percentage of contamination caused by the cytosolic
and chloroplastic marker, TPI.
Determination of the ASC/GSH Pool
Apoplastic ASC and DHA and apoplastic GSH and GSSG
contents were directly determined in the IWF by HPLC, according
to Jiménez et al. (1997)
. Reduced and oxidized ASC and GSH were
extracted with 2% (w/v) metaphosphoric acid from the leaf material
resulting from the IWF extraction, and measured as described by
Jiménez et al. (1997)
.
SOD Activity
Total SOD activity was assayed, in the absence and in the
presence of KCN, by the ferricytochrome c method using
xanthine/xanthine oxidase as the source of
O2.
radicals (McCord and Fridovich, 1969
).
SOD activity was corrected by the percentage of contamination caused by
the cytosolic and chloroplastic marker, TPI. To separate SOD isozymes,
non-denaturing PAGE and isoelectrofocusing were performed on 10% and
6% (w/v) acrylamide gels, respectively, using a mini protean
II dual slab cell (Bio-Rad, Hercules, CA). The range of
ampholytes (Pharmacia) used were: pH 3.5 to 5, pH 4.2 to 5.4, and pH
3.5 to 7.0. Samples were prefocused at 150 V for 30 min, and then
focused at 250 V for 1 h 30 min. SOD isozymes were localized by
the photochemical method of Weissiger and Fridovich (1973)
. Isoenzyme
identification was performed by selective inhibition with KCN or
H2O2 (Hernández et al., 1999
). The
percentage of activity for the different SODs was quantified by
recording the transmittance of gels in a CS-9000 densitometer
(Shimadzu, Kyoto).
Class III Peroxidase Activity and Isoenzyme Analysis
Class III peroxidase activity in IWF was determined in assays
containing 50 mM Tris-acetate buffer (pH 5.0) and 0.5 mM H2O2, using the following
electron donors: 0.1 mM coniferyl alcohol (
262 = 9,600 M
1
cm
1), 0.1 mg mL
1 tetramethylbenzidine-HCl
(
652 = 39,000 M
1
cm
1), and 1.0 mM 4-methoxy-
-naphtol
(
595 = 21,600 M
1
cm
1; Ros Barceló, 1998
). The reaction was initiated
by adding enzyme. Controls were carried out in the absence of
H2O2.
Class III peroxidase isoenzymes were separated by isoelectric focusing
in 3.5 to 10.0 pH gradients as described by Ferrer and Ros
Barceló (1999)
, and stained with 4-methoxy-
-naphtol for 1 h at 25°C using a reaction medium identical to that described above.
Controls were carried out in the absence of
H2O2.
Determination of Protein Content
Protein content was estimated according to Bradford (1976)
using
bovine serum albumin as standard.
Histochemical Detection of H2O2 and
O2.
in Pea Leaves
The histochemical detection of H2O2 and
O2.
in pea leaves was performed as described
by Schraudner et al. (1998)
with minor modifications. In the case of
H2O2 we used an endogenous peroxidase-dependent in situ histochemical staining, in which leaf quarters were vacuum infiltrated with 0.1 mg mL
1 3,3'-diaminobenzidine in 50 mM Tris-acetate buffer (pH 5.0) and incubated at 25°C in
the dark for 24 h. Controls were performed in the presence of 10 mM ascorbic acid.
The histochemical detection of O2.
was
performed by infiltrating leaf quarters directly with 0.1 mg
mL
1 NBT in 25 mM K-HEPES
[4-(2-hydroxyethyl)-1-piperazineethanesulfonic acid] buffer (pH
7.6) and incubating at 25°C in the dark for 2 h. Controls in the
presence of both 10 mM MnCl2 and/or 100 units mL
1 SOD were performed. The
O2.
-removing compounds (MnCl2 and
SOD) were directly added to the infiltration buffer.
In both cases, leaf quarters were rinsed in 80% (v/v) ethanol for 10 min at 70°C, mounted in lactic acid:phenol:water (1:1:1, v/v), and photographed directly using an SZX 12 microscope (Olympus. Kyoto).
| |
FOOTNOTES |
|---|
Received February 21, 2001; returned for revision April 28, 2001; accepted July 17, 2001.
1 This work was supported by the Dirección General de Ensenñanza Superior e Investigación Científica, Spain (project no. PB95-004-02), by the Ministerio de Educación y Cultura, Spain (project no. PB-97-1042), by the European Union (project no. FAIR-CT-98-5020), and by the University of Murcia (postdoctoral fellowship to M.A.F.).
* Corresponding author; e-mail fsevilla{at}natura.cebas.csic.es; fax 34-968-396213.
Article, publication date, and citation information can be found at www.plantphysiol.org/cgi/doi/10.1104/pp.010188.
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