jurnal nutan 2gggsrfgrrrrrrrrrgsrgggggggggggggggggggggggggggggggggggggggggg
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This article was downloaded by: [ade maskar]On: 14 April 2015, At: 04:56Publisher: Taylor & FrancisInforma Ltd Registered in England and Wales Registered Number: 1072954 Registered office: Mortimer House,37-41 Mortimer Street, London W1T 3JH, UK
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Comparison of inorganic solute accumulation in shoots,radicles and cotyledons of Vicia cracca during theseedling stage under NaCl stressYing Wang a , Jiyun Yang b , Shicheng Jiang b , Yu Tian b , Haixia Sun a , Minling Wang a ,Guangdi Li a & Daowei Zhou aa Northeast Institute of Geography and Agroecology, Chinese Academy of Sciences ,Changchun , Chinab Key Laboratory of Vegetation Ecology of Ministry of Education, Institute of GrasslandScience, Northeast Normal University , Changchun , ChinaPublished online: 15 Feb 2012.
To cite this article: Ying Wang , Jiyun Yang , Shicheng Jiang , Yu Tian , Haixia Sun , Minling Wang , Guangdi Li & Daowei Zhou(2012) Comparison of inorganic solute accumulation in shoots, radicles and cotyledons of Vicia cracca during the seedlingstage under NaCl stress, Soil Science and Plant Nutrition, 58:1, 24-31, DOI: 10.1080/00380768.2011.647606
To link to this article: http://dx.doi.org/10.1080/00380768.2011.647606
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Soil Science and Plant Nutrition (2012), 58, 24—31 http://dx.doi.org/10.1080/00380768.2011.647606
ORIGINAL ARTICLE
Comparison of inorganic solute accumulation in shoots, radiclesand cotyledons of Vicia cracca during the seedling stage underNaCl stress
Ying WANG1, Jiyun YANG2, Shicheng JIANG2, Yu TIAN2, Haixia SUN1,Minling WANG1, Guangdi LI1 and Daowei ZHOU1
1Northeast Institute of Geography and Agroecology, Chinese Academy of Sciences, Changchun, China and 2Key Laboratory of
Vegetation Ecology of Ministry of Education, Institute of Grassland Science, Northeast Normal University, Changchun, China
Abstract
In the present study, differences in inorganic solute accumulation in shoots, radicles and cotyledons during the
seedling stage of Vicia cracca Linn were evaluated in response to a range of sodium chloride (NaCl)
concentrations. Seeds were sown in Petri dishes, germinated and grown with NaCl treatment for 10 days in a
growth chamber, with a temperature of 20�C and a 12 h light/dark cycle. Results showed that percentage
germination, germination rate, fresh weight and dry weight, and relative water content decreased as the NaCl
concentration increased in shoots, radicles and cotyledons. There were no significant differences in dry
weight/fresh weight ratios in shoots and radicles among treatments. However, the dry weight/fresh weight
ratio in cotyledons was significantly higher at 200 mM NaCl compared to treatments with lower NaCl
concentrations. Sodiumþ and Cl� concentrations in shoots and radicles increased as the NaCl concentration
increased. Sodiumþ and Cl� concentrations in shoots and radicles were much higher than those in cotyledons.
Similar trends were found for Kþ, Ca2þ, Mg2þ, H2PO�4 . By contrast, SO2�4 concentrations were lower in
shoots and radicles than in cotyledons, while NO�3 concentrations were similar in shoots, radicles and
cotyledons. In particular, Kþ efflux was observed in shoots, radicles and cotyledons when no salt stress was
imposed. In summary, increased NaCl concentration had adverse effects on germination and post-
germination growth. Inorganic ion accumulation in shoots and radicles was high, which might function in
osmotic adjustment in those plant organs. By contrast, inorganic ion accumulation did not occur in
cotyledons, suggesting that in cotyledons osmotic adjustment might not function the same way as in shoots
and radicles, because cotyledons function mainly as storage for carbohydrates or inorganic ions.
Key words: organ types, salinity, osmotic adjustment, solutes, Vicia cracca.
INTRODUCTION
Soil salinity is a major abiotic stress influencing plant
growth and productivity worldwide. About 7% of the
world’s total land area experiences soil salinity problems
(Musyimi 2005). High salt (NaCl) concentrations result in
ionic imbalance and hyperosmotic stress in plants (Zhu
2001), a significant concern due to its potential to
decrease agricultural production, especially in arid and
semiarid regions of the world (Pesarraki 1999). In these
regions, salinity is one of the limiting factors for plant
growth (Sanchez et al. 1998; Shannon et al. 1994). High
salinity disrupts homeostasis in water potential and ion
distribution (Zhu 2001). There is also evidence that salt
tolerance is a complex physiological trait affecting the
entire life history of a plant (Flowers 2004). Halophytes
are tolerant to salinity partly because they can uptake
water by maintaining a high osmotic potential through
accumulation of inorganic and organic solutes (Bradley
and Morris 1991; Martınez-Ballesta et al. 2004). On the
other hand, saline tolerance in glycophytes is associated
Correspondence: Daowei ZHOU, 3195 Weishan Road,Changchun 130012, P. R. China. Tel: þ860431-85542206.Fax: þ860431-85542206. Email: [email protected] 31 December 2010.Accepted for publication 4 December 2011.
� 2012 Japanese Society of Soil Science and Plant Nutrition
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with the capacity to limit uptake and/or transport of saline
ions (mostly sodium [Naþ] and chloride [Cl�]) from the
root zone to aerial parts (Greenway and Munns 1980).
In saline environments, seeds and seedlings are often
exposed to higher salt concentrations relative to older
plants because germination typically occurs at or near the
soil surface (Foolad 1999). Germination and seedling
growth, particularly of young seedlings, are vulnerable to
environmental conditions and growth will be determined
by both macro- and micro-site conditions (Malcolm et al.
2003). Salinity reduces or delays germination and post-
germination growth (Fooland and Lin 1997). The first
physiological disorder, which takes place during germi-
nation, is the reduction in imbibition of water by seeds
due to a low solute potential in the saline growth media
to adapt the salinity condition. In different plant species
it was found that salinity caused accumulation of
inorganic solutes, such as Naþ and Cl�, in seedlings
(Ashraf et al. 2003; de Lacerda et al. 2003; Meloni et al.
2008; Ungar 1996).
Vicia cracca L. (Fabaceae) is native to central Asia and
Europe, and has been naturalized in almost all of North
America. The species is one of the most common fodder
plants in Northern China. V. cracca is a wild high-
quality forage widely grown mostly for hay, green
forage, silage or grain. It is a hypogeal-germinating
legume species. The cotyledons are typical embryonic
leaves and therefore function as carbohydrate storage,
but in some cases the cotyledons remain enclosed in the
seed coat, and function exclusively as a food reserve
(Garwood 1996; Kitajima 1992).
To date, the majority of published works on species or
cultivars under NaCl stress has been completed with
older plants (Guo et al. 2009; Zhang and Mu 2009;
Yang et al. 2008). There is limited information on the
salt tolerance of V. cracca during germination and post-
germination growth. The objective of this study was to
compare the inorganic solute accumulation in shoots,
radicles and cotyledons of V. cracca during the seedling
stage in response to different level of NaCl stress.
MATERILAS AND METHODS
Plant materials, germination and seedlingharvest
Seeds used in this study were harvested from the
Ecological Research Station for Grassland Farming,
Chinese Academy of Sciences, Changling, Jiling, China
(44�330N, 123�310E) and stored at 4�C. Prior to the
experiment, seeds were treated with 98% sulfuric acid
(H2SO4) for 25 min to promote germination. Seeds were
then washed thoroughly with distilled water.
Germination was conducted on 100-seed samples
placed on moist blotter paper in 90 mm Petri dishes.
Petri dishes were placed in a growth cabinet for 10 d at
20�C and a 12 h light/dark cycle daily.
The experiment was arranged in a completely ran-
domized design with four treatments and four replicates.
The treatments were 0, 50, 100 and 200 mM NaCl. At
the start of the experiment, about 10 mL of solution with
the designated concentration of NaCl was added to each
Petri dish, so that about half the volume of each seed was
immersed. Distilled water was used for a treatment with
0 mM NaCl as control. The experiment was repeated
three times.
Germination rate was determined by the radicle
penetrating the seed coat. The number of seeds germi-
nated was counted every day to determine percentage
germination and germination rate. The germination rate
was estimated using a modified Timson index of germi-
nation velocity¼P
G/t, where G is the percentage seed
germination at 1-d intervals and t is the total germination
period (Khan and Ungar 1984). The maximum possible
value of this index is 100.
Growth parameters and relative water content
The seedlings were washed with distilled water on
day 10. Seedlings were dissected into cotyledon, radicle
and shoot (the remaining part). The seed coat was
removed if attached before harvesting.
The relative water contents (RWC) of shoot, radicle
and cotyledon were calculated using the following
equation according to Silveira et al. (2003).
RWC ¼FW�DW
TW�DW� 100
where FW is the fresh weight, TW is the turgid weight
measured after 24 h of saturation in distilled water in
Petri dishes at 4�C in the dark, and DW is the dry weight
measured after drying at 70�C for 48 h to a constant
weight. Fifty replications were used. Few shoots emerged
from the seed coat under the 200 mM NaCl treatment;
therefore only radicles and cotyledons were harvested
and their weights measured. The seed coat was removed
before harvesting.
Determination of inorganic solutes
The cotyledons, shoots and radicles were oven-dried at
105�C for 15 min and then subsequently dried at a
second time at 70�C for 48 h to a constant weight at the
time of harvest. Dry samples (50 mg) were treated with
10 mL deionized water at 100�C for 1 h, the homogenate
was centrifuged at 3000 g for 10 min and filtered, and the
filtrate was used to determine free inorganic ion content.
All soluble contents were expressed in mmol g�1 DW.
Inorganic solute accumulation in Vicia cracca 25
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An atomic absorption spectrophotometer (TAS-990;
Purkinje General, Beijing, China) was used to determine
the Naþ, potassium (Kþ) and calcium (Ca2þ) content.
Anions (Cl�, nitrate [NO�3 ], dihydrogen phosphate
[H2PO�4 ] and sulfate [SO2�4 ]) were determined by ion
chromatography (DX-300 ion chromatographic system;
AS4A-SC ion-exchange column, CDM-II electrical con-
ductivity detector, mobile phase: Na2CO3/NaHCO3¼
1.7/1.8 mmol L�1; DIONEX, Sunnyvale, CA, USA).
Data analysis
Data were analyzed using a one-way Analysis of
Variance (ANOVA) in SPSS statistical software version
12.0 (SPSS Inc, Chicago Illinois, USA). Tests of signif-
icant differences among treatments were analyzed using
the Least Significant Difference (LSD) test at P50.05.
RESULTS
Germination and seedling growth
Percentage germination and germination rate decreased
with increased salt treatment levels (Table 1). Shoot and
radicle FW exhibited similar trends with germination
parameters, while the cotyledon FW presented a signif-
icant reduction at 200 mM NaCl compared to the
control (Table 2). Salinity markedly decreased both
shoot and radicle DW. However, no significant change
was observed among different levels of NaCl stress. The
mean weight was 10.39 mg for cotyledon DW (Table 2).
There were no significant differences in shoot and
radicle DW/FW ratios among treatments. However,
DW/FW ratio of cotyledons increased significantly
under the 200 mM NaCl treatment. Shoot, radicle and
cotyledon RWC reduced significantly under NaCl stress
compared to the control (Table 2).
Inorganic solutes
Cation concentrations in shoots and radicles were similar,
but both higher than those in cotyledons (Fig. 1).
Sodiumþ levels increased significantly in shoots and
radicles as well as significantly increased in cotyledons
as the concentration of NaCl increased. A similar pattern
was found for Kþ concentrations in shoots and radicles,
but cotyledon Kþ concentration increased from 0 to
100 mM NaCl, and then decreased significantly at
200 mM NaCl (Fig. 1b). Calcium2þ concentrations in
seedlings were lower compared to other cation concen-
trations (Fig. 1c). With increasing salinity levels, Ca2þ
concentration in shoots increased significantly.
Calcium2þ concentration in radicles was higher at
200 mM NaCl compared to the control. There was no
significant change in cotyledon Ca2þ concentration with
increased NaCl concentration. Overall, Ca2þ concentra-
tions were higher in shoots and radicles than in cotyle-
dons (Fig. 1c). There were no differences in shoot and
cotyledon magnesium (Mg2þ) concentrations among
treatments (Fig. 1d). Magnesium2þ concentrations in
radicles increased at 50, 100, and 200 mM NaCl
compared with the control plants.
With respect to anion concentrations, the Cl� concen-
trations exhibited similar trends to Naþ in shoots,
radicles and cotyledons (Fig. 2a). There were no signif-
icant differences in cotyledon NO�3 concentrations with
various NaCl concentrations. However, the shoot and
radicle NO�3 concentrations increased significantly at 50
and 100 mM NaCl compared to the control (Fig. 2b).
The H2PO�4 concentrations in shoots, radicles and
cotyledons remained unchanged from 0 to 100 mM
Table 2 Fresh weight (FW), Dry weight (DW), DW/FW ratiosand relative water content (RWC) (mean� SE) in cotyledons,shoots and radicles of V. cracca under NaCl stress
Cotyledon Shoot Radicle
FW (mg)0 26.91� 0.72a
y 7.81� 0.40a 4.07� 0.28a
50 25.48� 0.94ab 6.79� 0.22b 3.18� 0.21b
100 26.23� 0.57a 5.25� 0.26c 2.94� 0.15b
200 23.28� 1.21b — 1.47� 0.10c
DW (mg)0 9.95� 0.34a 0.54� 0.04a 0.45� 0.05a
50 10.48� 0.54a 0.50� 0.02a 0.28� 0.02b
100 10.51� 0.21a 0.35� 0.02b 0.26� 0.02bc
200 10.63� 0.73a — 0.15� 0.04c
DW/FW ratios0 0.369� 0.004b 0.069� 0.003a 0.084� 0.006a
50 0.412� 0.017b 0.073� 0.001a 0.087� 0.003a
100 0.402� 0.012b 0.067� 0.002a 0.088� 0.005a
200 0.459� 0.011a — 0.102� 0.004a
RWC (%)0 98.16� 0.38a 96.15� 0.52a 95.54� 0.55a
50 95.19� 0.29b 90.66� 0.56b 92.39� 0.76b
100 90.31� 0.23c 90.83� 0.42b 92.40� 0.70b
200 82.11� 1.37d — 88.24� 1.17c
yWithin a column, means followed by the same letter are not significantly
different at P¼0.05.
Table 1 Percentage germination and germination rate(mean� SE) of V. cracca L. under sodium chloride (NaCl) stress
Percentagegermination (%)
Germinationrate (Number d�1)
0 96� 1.5ay 58� 1.7a
50 86� 0.3b 39� 0.7b
100 85� 0.9b 31� 0.9c
200 20� 1.0c 3� 0.2d
yWithin a column, means followed by the same letter are not significantly
different at P¼0.05.
26 Y. Wang et al.
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NaCl, but slightly and significantly decreased at 200 mM
NaCl in radicles and cotyledons. The H2PO�4 concen-
trations in shoots and radicles were higher than in
cotyledons (Fig. 2c). There were no significant differences
in SO2�4 concentrations in shoots and radicles among all
the NaCl levels. The cotyledon SO2�4 concentration
remained unchanged from 0 to 100 mM NaCl and
decreased significantly at 200 mM NaCl. The SO2�4
concentration was greater in cotyledons than in shoots
and radicles (Fig. 2d). The Kþ/Naþ ratio decreased as salt
stress increased in shoots and cotyledons, but remained
unchanged in radicles from 0 to 100 mM NaCl. The
radicle Kþ/Naþ ratio was significantly lower at 200 mM
NaCl compared to the control (Fig. 3).
DISCUSSION
In saline environments, salt concentrations result in plant
vulnerability to many environmental stresses. Therefore,
adaptation to salinity is crucial for establishment of
species (Koyro and Sayed 2008). Results from the present
study showed that salinity affected seed germination and
post-germination growth. There are several possible
explanations. First, salinity could reduce the ability of
the plant to take up water, leading to slower growth
(Munns et al. 2006). This is the osmotic or water-deficit
effect of salinity. Salt stress exerts effects on water
relationships in both halophytic and glycophytic species
(Yeo and Flowers 1980; Djanaguiraman et al. 2006). In
the present study, RWC in shoot, radicle and cotyledon
followed a similar pattern and decreased with salt
concentrations. In most plants, the solute content of
cells at high salinity is higher than in non-saline
conditions, largely due to accumulation of ions (e.g.
Naþ and Cl�) and organic solutes. During rehydration to
establish turgid weight, the higher solute content in salt-
treated than in untreated shoots, radicles and cotyledons
causes a greater water uptake in the former than the
later. This results in a significantly low RWC with
salinity concentrations (Munns et al. 2006). This result is
consistent with previous studies (Meloni et al. 2008;
Ruffino et al. 2010) although RWC was not a useful
0
0.3
0.6
0.9
1.2N
a+ (
mm
olg–1
DW
)
Cotyledon Shoot Radicle
(a)
a''aa'a
abbb
b''a
c'b
b'b
c''a
d''a ccdc
0
1.2
2.4
3.6
4.8
K+ (
mm
olg–1
DW
)
(b)
bb ac ab bb
a''aa''aa''a
b''a
a'a
a'b
b'a'
0
0.06
0.12
0.18
0.24
NaCl (mM)
Mg2+
(m
mol
g–1D
W)
(d)
abab
ab ab
a'a
a'a a'a
b''a
a''a
a''aa''a
0
0.0003
0.0006
0.0009
0.0012
0 50 100 2000 50 100 200NaCl (mM)
NaCl (mM)0 50 100 2000 50 100 200
NaCl (mM)
Ca2+
(m
mol
g–1
DW
)
(c)
a''a
b''a
a''aa''a
ab
abab
ab
a'a
a'a
b'b
Figure 1 Effects of salt stress on the contents of (a) sodium (Naþ), (b) potassium (Kþ), (c) calcium (Ca2þ) and (d) magnesium (Mg2þ)in shoots, radicles and cotyledons of V. cracca L. Means followed by different letters of a, b and c for cotyledon (a0, b0 and c0 for shootand a0 0, b0 0 and c0 0 for root) are significantly different at P50.05. Means followed by different letters of a, b, and c among the sametreatments are significantly different at P50.05.
Inorganic solute accumulation in Vicia cracca 27
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indicator of turgor in salt-treated plants undergoing
osmotic adjustment. In the present study, it was observed
that cotyledon RWC was similar to shoot and radicle
RWC although ionic concentrations were lower in
cotyledons. Generally, plants can reduce water content
as a quick and economical approach to reduce cell water
potential in response to osmotic stress (Lissner et al.1999).
Second, plants are subject to the toxic effects of salt
inside the plant. Inhibition in germination and post-
germination growth can be related to high transport of
Naþ and Cl� to shoot and radicle from the saline growth
media. This is the salt specific or ion-excess effect of
salinity. The excessive accumulation of inorganic ions,
especially Naþ and Cl�, often results in toxicity, which is
the main cause of growth inhibition induced by salinity
(Khan et al. 2000; Yang et al. 2007). In our study, Naþ
and Cl� concentrations in cotyledons, shoots and radi-
cles increased from 0 to 100 mM NaCl (Figs 1 and 2). An
accumulation of high Naþ and Cl� concentrations in
0
0.02
0.04
0.06
NaCl (mM)
SO42–
(mm
olg–1
DW
)
(d)
aa
aaaa
baa'b a''b
a'ba''ba''b
a''ba'b
0
0.2
0.4
0.6
0 50 100 2000 50 100 200
NaCl (mM)
H2P
O4– (m
mol
g–1D
W)
(c)
ab bbab ab
a'a a'aa'a
a''ab''a
a''a a''a
0
1
2
3C
l– (mm
olg–1
DW
)
CotyledomShootRadicle
(a)
abcb ac bbc'b
b'b
a'a
d''a
c''a
b''a
a''a
0
0.002
0.004
0.006
0.008
NO
3 (m
mol
g–1
DW
)–
(b)
b'a
a'aa'a
b''a
a''aa''a a''aaa aa
aaaa
Figure 2 Effects of salt stress on the contents of (a) chlorine (Cl�), (b) nitrate (NO�3 ), (c) dihydrogen phosphate (H2PO�4 ) and(d) sulfate (SO2�
4 ) in shoots, radicles and cotyledons of V. cracca. Means followed by different letters of a, b and c for cotyledon (a0, b0
and c0 for shoot and a0 0, b0 0 and c0 0 for root) are significantly different at P50.05. Means followed by different letters of a, b, and camong the same treatments are significantly different at P50.05.
0
20
40
60
80
0 50 100 200NaCl (mM)
K+/N
a+
Cotyledon Shoot Radicle
aA
bB
a'B
b'A b'AbA bAa''B a''A a''b''A b''A
Figure 3 Effects of salt stress on the Kþ/Naþ ratios in shoots,radicles and cotyledons of V. cracca. Means followed bydifferent letters of a, b and c for cotyledon (a0, b0 and c0 forshoot and a0 0, b0 0 and c0 0 for root) are significantly different atP50.05. Means followed by different letters of A, B, and Camong the same treatments are significantly different atP50.05.
28 Y. Wang et al.
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radicles and shoots may indicate the presence of an
inhibition mechanism for Naþ and Cl� transport to
cotyledons, which may protect or alleviate cotyledon
damage.
In addition, inorganic solute accumulation may func-
tion in osmotic adjustment in shoots and radicles because
increase of the inorganic solutes is one of the factors used
to adjust osmotic potential. Significant entry of Naþ will
result in severe growth reduction or death in sensitive or
glycophytic species, but may benefit halophytes, or lead
to mild toxicity symptoms in salt-tolerant species. The
ability of a plant to adjust high osmotic potential as a
result of excess of Naþ and Cl� in cells is vital for growth
maintenance. In the present study, the Naþ and Cl�
concentrations in shoots and radicles were much higher
than those found in cotyledons and a similar tendency
was observed in the concentration of most important
inorganic solute components. The difference of inorganic
solute accumulation between cotyledons and other
tissues might be due to their different anatomical
structures. Cotyledons function as carbohydrate storage
and contain large amounts of reserve substances (Alche
et al. 2006). During seed development, there are few
vacuoles formed in cotyledons although large vacuoles
compartmentalization takes place accompanied by a
decrease in the reserve substances (Alche et al. 2006). It is
well known that ions acquired in excess of immediate
requirements are mainly accumulated and stored in
vacuoles of mature cells (Karley et al. 2000). Therefore,
cotyledons accumulated relatively smaller amounts of
inorganic solutes, especially Naþ and Cl�, than did
shoots and radicles.
The present study also indicated that shoots and
radicles share a similar salt inclusion strategy to deal with
excessive salinity. In this process, the shoot and radicle
tissues were adapted to accumulate large amounts of
saline ions, always greater than the amounts in cotyle-
dons. Despite direct absorption of solutes from the
growth media by the embryo, the germinated seed
transfers most of its inorganic and organic reserves to
the growing tissues. Thus the mechanism of salt tolerance
is likely to become very complex at this stage compared
with other stages. Voigt et al. (2009) suggested that salt-
induced inhibition of seedling growth is narrowly coor-
dinated with the delay of reserve mobilization and the
accumulation of products of reserve hydrolysis in the
cotyledons.
Potassiumþ is essential to all plant life, and in most
terrestrial plants, Kþ is the major cationic inorganic
nutrient. Salinity tolerance typically relies on limiting
Naþ accumulation and maintaining Kþ concentration in
the cytosol to balance ionic homeostasis (Flowers et al.
1977). Therefore, one of the key elements in salinity
tolerance is the capacity to maintain a high cytosolic
Kþ/Naþ ratio, as stated by Yeo (1998). In our study, the
Kþ/Naþ ratios decreased at 50, 100, and 200 mM NaCl
in all three plant organs. The lower endogenous Kþ
concentration in both shoots and radicles at control may
contribute to Kþ efflux and translocation (Al-Karakia
2001; Maathuis and Amtmann 1999), as Kþ was not
contained in the treatment media. However, Kþ concen-
tration in cotyledons decreased significantly at 200 mM,
compared with 50 and 100 mM, NaCl. This finding was
similar to that found in wheat embryos (Petruzzelli et al.
1991; Cramer et al. 1994). Nassery (1979) and Rehman
et al. (1996) reported that the toxic effect of salts in seeds
is usually caused by a reduction in seed Kþ concentra-
tion. Khan et al. (2000) indicated that decreases in
endogenous Kþ levels induced by high external NaCl
concentrations can be attributed to a transmembrane
competition between Kþ and Naþ fluxes. However, it
seemed in our study that competitive inhibition between
Kþ and Naþ fluxes did not exist because Kþ concentra-
tions in shoots and radicles remained higher than in
cotyledons, which may reflect a lack of transfer of
cytosolic Kþ from shoots and radicles to cotyledons.
Sodiumþ, Cl� and Kþ are important saline ions for
total osmotic adjustment. In the present study, seedlings
maintained a high Kþ concentration in shoots and
radicles to keep a high osmotic potential from 50 to
100 mM NaCl stresses, which would enhance the
salinity tolerance of V. cracca. It is suggested that
supplemental K may increase the Kþ/Naþ ratio and
hence would strengthen the salinity tolerance of crops
or cultivars during germination and post-germination
growth. The ability of species or cultivars to survive
during the germination and early seedling stages is
crucial for future improvement of crop yield. In the
present study, the behavior of Kþ and Naþ was
different from Ca2þ and Mg2þ in the response of
plants to salt stress (Yang. 2007). Magnesium2þ is the
key component of chlorophyll and Ca2þ can maintain
membrane stability, help to form cell walls and take
part in signal transduction. Though Ca2þ and Mg2þ
increased significantly under salt stress as compared to
the control, it can be concluded that their contributions
to osmotic adjustment were small because the concen-
trations of Ca2þ and Mg2þ were very low compared to
those of Kþ and Naþ.
In summary, increased NaCl concentration had
adverse effects on germination and post-germination
growth. Inorganic ion accumulation in shoots and
radicles was high, which might function in osmotic
adjustment in those plant organs. These results were not
seen in the cotyledons, probably because cotyledons
mainly function as storage of carbohydrates and inor-
ganic substances.
Inorganic solute accumulation in Vicia cracca 29
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ACKNOWLEDGMENTS
This work was financed by the National NaturalScience Foundation of China (30970493) and Projectsin the National Science & Technology Pillar Program(2009BADB3B02).
REFERENCES
Alche JD, Jimenez-Lopez JC, Wang W, Castro AJ, Rodrıguez-
Garcıa MI 2006: Biochemical characterization and cellular
localization of 11S type storage proteins in olive (Olea
europaea L.) seeds. J. Agric. Food Chem., 54, 5562–5570.
Al-Karakia GN 2001: Germination, sodium, and, potassium
concentrations of barley seeds as influenced by salinity.
J. Plant Nutr., 24, 511–522.
Ashraf MR, Zafar R, Ashraf MY 2003: Time-course changes in
the inorganic and organic components of germinating
sunflower achenes under salt (NaCl) stress. Flora,
198, 26–36.
Bradley PM, Morris JT 1991: Relative importance of ion
exclusion, secretion and accumulation in Spartina alterni-
flora Loisel. J. Exp. Bot., 42, 1525–1532.
Cramer GR, Alberico GJ, Schmidt C 1994: Leaf expansion
limits dry matter accumulation of salt-stressed maize. Aust.
J. Plant Physiol., 21, 663–674.
de Lacerda CF, Cambraia J, Oliva MA, Ruiz HA, Prisco JT
2003: Solute accumulation and distribution during shoot
and leaf development in two sorghumgenotypes under salt
stress. Environ. Exp. Bot., 49, 107–120.
Djanaguiraman M, Sheeba JA, Shanker AK, Devi DD,
Bangarusamy U 2006: Rice can acclimate to lethal level
of salinity by pre-treatment with sublethal level of salinity
through osmotic adjustment. Plant Soil, 284, 363–373.
Flowers TJ 2004: Improving crop salt tolerance. J. Exp. Bot.,
55, 307–319.
Flowers TJ, Troke PF, Yeo AR 1977: The mechanism of salt
tolerance in halophytes. Ann. Rev. Plant Biol., 28, 89–121.
Foolad MR 1999: Comparison of salt tolerance during seed
germination and vegetative growth in tomato by QTL
mapping. Genome, 42, 727–734.
Foolad MR, Lin GY 1997: Absence of a genetic relationship
between salt tolerance during seed germination and vege-
tative growth in tomato. Plant Bree., 116, 363–367.
Garwood NC 1996: Functional morphology of tropical tree
seedlings. In The Ecology of Tropical Forest Tree
Seedlings, Ed. MD Swaine, pp 59—129, Parthenon
Publishing Group, Carnforth, UK.
Greenway H, Munns R 1980: Mechanisms of salt tolerance in
non-halophytes. Ann. Rev. Plant Biol., 31, 149–190.
Guo R, Shi LX, Yang YF 2009: Germination, growth, osmotic
adjustment and ionic balance of wheat in response to saline
and alkaline stresses. Soil Sci. Plant Nutr., 55, 667–679.
Karley AJ, Leigh RA, Dale S 2000: Where do all the ions go?
The cellular basis of differential ion accumulation in leaf
cells. Trends Plant Sci., 5, 465–470.
Khan MA, Ungar IA 1984: The effect of salinity and temper-
ature on the germination of polymorphic seeds and growth
of Atriplex triangularis Willd. Am. J. Bot., 71, 481–489.
Khan MA, Ungar IA, Showalter AM 2000: Effects of salinity on
growth, water relations and ion accumulation of the
subtropical perennial halophyte, Atriplex griffithii var.
stocksii. Ann. Bot., 85, 225–232.
Kitajima K 1992: Relationships between photosynthesis and
thickness of cotyledons for tropical tree species. Fun. Ecol.,
6, 582–589.
Koyro HW, Sayed SE 2008: Effect of salinity on composition,
viability and germination of seeds of Chenopodium quinoa
Willd. Plant Soil, 302, 79–90.
Lissner J, Schierup HH, Com{n FA, Astorga V 1999: Effect of
climate on the salt tolerance of two Phragmites australis
populations. I. Growth, inorganic solutes, nitrogen rela-
tions and osmoregulation. Aquat. Bot., 64, 317–333.
Maathuis FJM, Amtmann A 1999: Kþ nutrition and Naþ
toxicity: the basis of cellular Kþ/Naþ Ratios. Ann. Bot.,
84, 123–133.
Malcolm CV, Lindley VA, O’Leary JW, Runciman HV, Barrett-
Lennard EG 2003: Halophyte and glycophyte salt toler-
ance at germination and the establishment of halophyte
shrubs in saline environments. Plant Soil, 253, 171–185.
Martınez-Ballesta MC, Martınez V, Carvajal M 2004: Osmotic
adjustment, water relations and gas exchange in pepper
plants grown under NaCl or KCl. Environ. Exp. Bot.,
52, 161–174.
Meloni DA, Gulotta MR, Martınez CA 2008: Salinity tolerance
in Schinopsis quebracho colorado: seed germination,
growth, ion relations and metabolic responses. J. Arid
Environ., 72, 1785–1792.
Munns R, James RA, Lauchli A 2006: Approaches to increasing
the salt tolerance of wheat and other cereals. J. Exp. Bot.,
57, 1025–1043.
Musyimi DM 2005: Evalution of young avocado plants for
tolerance to soil salinity by physiology parameter. (M.Sc
thesis). Maseno University, Maseno, Kenya.
Nassery H 1979: Salt-induced loss of potassium from plant
roots. New Phytol., 83, 32–37.
Pesarraki M 1999: Handbook of Plant and Crop Stress, Marcel
Dekker Inc., New York.
Petruzzelli L, Melillo MT, Bleve Zacheo TB, Marano B,
Taranto G 1991: The sensitivity of germinating Triticum
durum L. kernels to saline environment. Seed Sci. Res.,
1, 105–111.
Rehman S, Harris PJC, Bourne WF, Wilkin J 1996: The effect of
sodium chloride on germination and the potassium and
calcium contents of Acacia seeds. Seed Sci. Tech.,
25, 45–57.
Ruffino AMC, Rosa M, Hilal M, Gonzalez JA, Prado FE 2010:
The role of cotyledon metabolism in the establishment of
quinoa (Chenopodium qiunoa) seedlings growing under
salinity. Plant Soil, 326, 213–224.
Sanchez JM, Otero XL, Izco J 1998: Relationships between
vegetation and environmental characteristics in salt-marsh
system on the coast of Northwest Spain. Plant Ecol.,
136, 1–8.
30 Y. Wang et al.
Dow
nloa
ded
by [
ade
mas
kar]
at 0
4:56
14
Apr
il 20
15
![Page 9: jurnal nutan 2gggsrfgrrrrrrrrrgsrgggggggggggggggggggggggggggggggggggggggggg](https://reader035.vdocuments.mx/reader035/viewer/2022072008/55cf8f13550346703b98ac9b/html5/thumbnails/9.jpg)
Shannon MC, Grieve CM, Francois LC 1994: Whole-plant
response to salinity. In Plant Environment Interactions,
Ed. RE Wikinson, pp 199—244, M. Dekker Inc.,
New York.
Silveira JAG, de Almeida VR, da Rocha IMA, de OM,
Moreira AC, de Azevedo Moreira A, Oliveira JTA 2003:
Proline accumulation and glutamine synthetase activity are
increased by salt-induced proteolysis in cashew leaves.
J. Plant Physiol., 160, 115–123.
Ungar IA 1996: Effect of salinity on seed germination, growth
and ion accumulation of Atriplex patula
(Chenopodiaceae). Am. J. Bot., 83, 604–607.
Voigt EL, Almeida TD, Chagas RM, Ponte LFA, Viegas RA,
Silveira JAG 2009: Source-sink regulation of cotyledonary
reserve mobilization during cashew (Anacardium occiden-
tale) seedling establishment under NaCl salinity. J. Plant
Physiol., 166, 80–89.
Yang CW, Chong JN, Kim CM, Li CY, Shi DC, Wang DL
2007: Osmotic adjustment and ion balance traits of an
alkali resistant halophyte Kochia sieversiana during
adaptation to salt and alkali conditions. Plant Soil,
294, 263–276.
Yang CW, Shi DC, Wang DL 2008: Comparative effects of salt
and alkali stresses on growth, osmotic adjustment and
ionic balance of an alkaline-resistance halophyte Suaeda
glauca (Bge.). Plant Growth Regul., 56, 179–190.
Yeo AR 1998: Molecular biology of salt tolerance in the
context of whole-plant physiology. J. Exp. Bot.,
49, 915–929.
Yeo AR, Flowers TJ 1980: Salt tolerance in the halophyte
Suaeda maritime L. Dum.: evaluation of the effect of
salinity upon growth. J. Exp. Bot., 31, 1171–1183.
Zhang JT, Mu CS 2009: Effects of saline and alkaline stresses
on the germination, growth, photosynthesis, ionic balance
and anti-oxidant system in an alkali-tolerant leguminous
forage Lathyrus quinquenervius. Soil Sci. Plant Nutr.,
55, 685–697.
Zhu JK 2001: Plant salt tolerance. Trends Plant Sci., 6, 66–71.
Inorganic solute accumulation in Vicia cracca 31
Dow
nloa
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by [
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4:56
14
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il 20
15