Khadiga Alharbi1, Areej Ahmed Al-Osaimi2, Budour A Alghamdi3. 1. Department of Biology, College of Science, Princess Nourah bint Abdulrahman University, P.O. Box 84428, Riyadh 11671, Saudi Arabia. 2. Department of Biology, College of Science, Imam Abdulrahman Bin Faisal University, Dammam 34212, Saudi Arabia. 3. Genome Department, Ministry of Environment, Water and Agriculture, Riyadh 11564, Saudi Arabia.
Abstract
Salinity stress has a deleterious impact on plant development, morphology, physiology, and biochemical characteristics. Considering the NaCl-induced phytotoxicity, current investigation was done to better understand the salt-tolerant mechanisms using Pisum sativum L. (pea) as a model crop. Generally, NaCl resulted in a progressive decrease in germinative attributes and physiological and biochemical parameters of P. sativum (L.). The 400 mM NaCl level had a higher detrimental effect and reduced the germination rate, plumule, radicle length, and seedling vigor index (SVI) by 78, 89, 84, and 77%, respectively, under in vitro. Furthermore, after 400 mM NaCl exposure, physiological and enzymatic profiles like root dry biomass (71%) chl-a (66%), chl-b (54%), total chlorophyll (45%), and nitrate reductase activity (NRA) (59%) of peas were decreased. In addition, a NaCl dose-related increase in soluble protein (SP) and sugar (SS), Na+ and K+ ions, and stressor metabolites was recorded. For instance, at 400 mM NaCl, SP, SS, Na+ ion, K+ ion, root proline, and malondialdehyde (MDA) contents were significantly and maximally elevated by 65, 33, 84, 79, 85, and 89%, respectively, compared to the control (0 mM NaCl). Data analysis indicated that greater doses of pesticides dramatically increased reactive oxygen species (ROS) levels and induced membrane damage through production of thiobarbituric acid reactive substances (TBARS), as well as increased cell injury. To deal with NaCl-induced oxidative stress, plants subjected to higher salinity stress showed a considerable build-up in antioxidant levels. As an example, ascorbate peroxidase (APX), catalase (CAT), peroxidase (POD), and superoxide dismutase (SOD) were maximally and significantly (p ≤ 0.05) increased by 68, 80, 74, and 58%, respectively, after 400 mM NaCl exposure. The propidium iodide (PI)-stained and NaCl-treated plant roots corroborated the damaging effect of salinity-induced stress on the cell membrane, which was observed under a confocal laser microscope (CLSM). The cells exposed to 400 mM NaCl had maximum fluorescence intensity, indicating that higher level of salts can cause pronounced cell damage and reactive oxygen species (ROS) generation. The increases in superoxide ion (O2 -) and hydrogen peroxide (H2O2) content in NaCl-treated plant tissues indicated the elevation of ROS with increasing salt levels. This finding revealed that salt stress can cause toxicity in plants by causing alteration in metabolic activity, oxidative injury, and damage to cell membrane integrity.
Salinity stress has a deleterious impact on plant development, morphology, physiology, and biochemical characteristics. Considering the NaCl-induced phytotoxicity, current investigation was done to better understand the salt-tolerant mechanisms using Pisum sativum L. (pea) as a model crop. Generally, NaCl resulted in a progressive decrease in germinative attributes and physiological and biochemical parameters of P. sativum (L.). The 400 mM NaCl level had a higher detrimental effect and reduced the germination rate, plumule, radicle length, and seedling vigor index (SVI) by 78, 89, 84, and 77%, respectively, under in vitro. Furthermore, after 400 mM NaCl exposure, physiological and enzymatic profiles like root dry biomass (71%) chl-a (66%), chl-b (54%), total chlorophyll (45%), and nitrate reductase activity (NRA) (59%) of peas were decreased. In addition, a NaCl dose-related increase in soluble protein (SP) and sugar (SS), Na+ and K+ ions, and stressor metabolites was recorded. For instance, at 400 mM NaCl, SP, SS, Na+ ion, K+ ion, root proline, and malondialdehyde (MDA) contents were significantly and maximally elevated by 65, 33, 84, 79, 85, and 89%, respectively, compared to the control (0 mM NaCl). Data analysis indicated that greater doses of pesticides dramatically increased reactive oxygen species (ROS) levels and induced membrane damage through production of thiobarbituric acid reactive substances (TBARS), as well as increased cell injury. To deal with NaCl-induced oxidative stress, plants subjected to higher salinity stress showed a considerable build-up in antioxidant levels. As an example, ascorbate peroxidase (APX), catalase (CAT), peroxidase (POD), and superoxide dismutase (SOD) were maximally and significantly (p ≤ 0.05) increased by 68, 80, 74, and 58%, respectively, after 400 mM NaCl exposure. The propidium iodide (PI)-stained and NaCl-treated plant roots corroborated the damaging effect of salinity-induced stress on the cell membrane, which was observed under a confocal laser microscope (CLSM). The cells exposed to 400 mM NaCl had maximum fluorescence intensity, indicating that higher level of salts can cause pronounced cell damage and reactive oxygen species (ROS) generation. The increases in superoxide ion (O2 -) and hydrogen peroxide (H2O2) content in NaCl-treated plant tissues indicated the elevation of ROS with increasing salt levels. This finding revealed that salt stress can cause toxicity in plants by causing alteration in metabolic activity, oxidative injury, and damage to cell membrane integrity.
Salinity can arise
as a result of improper irrigation, drainage,
or fertilizer application, and it is most prevalent in protected farming.[1] Plants cultivated in saline areas have a number
of disadvantages. The very first and foremost is increased osmotic
stress caused by excessive salt concentrations in the soil solution,
which reduces the soil’s water potential.[2] The other drawback is increased concentrations of sodium
(Na+) and chloride (Cl–) ions, which
causes ionic imbalance by accumulating Na and Cl in tissues and inhibiting
the mineral nutrient uptake.[3] Although
plant species differ in their mechanisms of salinity tolerance,[4] salinity stress eventually reduces the plant
development.[5] Excessive levels of soil
salt can impede seed germination and seedling growth due to the combined
effects of high osmotic pressure and specific ion toxicity.[6] The production of many plant species declines
when exposed to excessive salinity, which is generally linked to a
drop in photosynthetic capability. A decrease in chlorophyll formation
can also cause a decrease in photosynthesis when the environment is
salinized.[7] In salt-sensitive plants, salinity
decreases/damages chlorophyll formation,[8,9] decreases the
photosynthetic pigments,[10] reduces the
photosynthetic[11] and transpiration rates,[12] and reduces stomatal conductance,[13] while it shows an increasing effect on salt-tolerant
plants. Salinity inhibits plant development by altering the turgor,
photosynthesis, and enzyme activity and it may cause leaf mortality
in older leaves.[14,15]After salt stress, apoptosis
(like degradation of DNA) has been
reported, resulting in successive nuclear degradation, cell death,
and retardation in the root development.[16] Salinity stress more often causes a build-up of reactive oxygen
species (ROS) in the roots and leaf tissues of plants at the cellular
level.[17] Plants have evolved a variety
of complex physiological and metabolic processes to cope with severe
environments, including a high number of stress-responsive genes and
the production of varied functional proteins via a complex signal
transduction network.[18] Plants can respond
to oxidative stress by increasing their antioxidant defenses. In aerobic
organisms, harmful byproducts of metabolic processes include superoxide
anion (O2–), hydrogen peroxide (H2O2), hydroxyl radical (OH•),
and other reactive oxygen species (ROS).[19] The coordinated functioning of ROS-scavenging pathways from different
cellular compartments may play a vital role in plant salt tolerance
by controlling the amount of ROS in cells, minimizing cellular damage,
and managing the ROS.[20,21]Plants use a variety of
antioxidant mechanisms to keep away these
toxic chemicals. Plants can regulate the activity of various antioxidant
enzymes and metabolites to keep ROS at a safe level when they are
stressed.[22] Superoxide dismutase (SOD),
peroxidase (POD), catalase (CAT), and peroxidase (POX) activity levels
are critical for a plant’s response to salinity stress.[23] These enzymes and metabolites not only protect
the plants from cellular damage but also regulate ROS levels to ensure
that their metabolic activities are optimum.[24] Furthermore, when plants are stressed by salt, they produce more
secondary metabolites such as soluble solids, sugars, organic acids,
proteins, and amino acids.Pea (Pisum sativum L.) is a widely
farmed vegetable and pulse crop. It is cultivated in the vicinity
of 1.1 million hectares worldwide, with a total production of 9.2
million tonnes and a yield of 8.35 tonnes per hectare.[25] Since pea has high levels of proteins, carbohydrates,
vitamins, and minerals such as iron (Fe), calcium (Ca), potassium
(K), and phosphorous (P) in thier nutritional composition, this therefore
makes it a valuable human dietary component.[26] It is also used to reduce cardiovascular problems due to its low
fat, salt, and cholesterol content.[27]The current study, which used P. sativum L. (garden pea) as a test/model crop, was designed to address the
serious concerns connected with salinity in legume cultivation. The
present work aimed at (i) evaluating the effect of increasing level
of NaCl on germination attributes of pea seeds cultivated both in vitro and in vivo, (ii) assessing the
salt-induced stress on biological features (growth, length, and dry
biomass) of peas, (iii) estimating the photosynthetic attributes (chlorophyll
and carotenoid) and nitrate reductase (NR) activity in NaCl-treated
pea foliages, (iv) determining the soluble protein, soluble sugar,
relative leaf water content (RLWC) and Na+/K+ ions in NaCl-induced peas, (v) evaluating the responses of increasing
NaCl levels on plant stress markers (proline and malondialdehyde content)
and antioxidant enzyme activity, and (vi) assessing the NaCl-induced
oxidative stress, cellular damage, and ROS generation (O2– and H2O2 content) in pea
organs.
Results and Discussion
NaCl Negatively Affected the Germination
Attributes and Vigor
Indices of Pea Seedling
Germination is a complex biological
process that requires several elements to operate simultaneously for
a seedling to emerge. Water intake is essential to activate the hydrolytic
enzymes that metabolize the seeds’ stored nutrients into simple
molecules, which are needed for cell growth and differentiation. The
presence of different abiotic stresses including salinity has an inhibitory
effect on seed germination. Salinity affects germination via changing
the osmotic component, which affects the ionic component, i.e., build-up
of Na and Cl.For the endurance and upholding of plant species,
the capacity of their seeds to sprout under a higher level of NaCl
in the soil is critical. Seed germination occurs in saline ecosystems
after heavy precipitation, i.e., when the soil salinity is low.[28] Here, P. sativum (L.) seeds germinated in the presence of 400 mM NaCl showed an 80%
reduction when compared to the control (Figure A). Increasing levels of salts can result
in osmotic and/or particular toxicity, which can lower the percentage
of seeds germination. Seeds treated with increasing levels of salt
had shorter plumule and radicle lengths than untreated control seeds.
For instance, a maximum and considerable decrease in length of plumule
(87%), radicle (74%), fresh weight (56%), and dry biomass (64%) was
recorded at 400 mM NaCl (Figure B–D). Like our observation, Baruah and Das[29] observed delayed germination in the presence
of elevated metal and salt concentrations. Similarly, different levels
of salt stress affected the germination efficiency and seedling development
in sorghum.[30] The degree of activity and
performance of seeds during germination and seedling emergence is
determined by the seedling vigor index. As a result, the most important
physiognomies of the seeds to be employed for cultivation are seed
germination and seedling vigor indices. In this study, with the increasing
level of salt concentrations (0–400 mM NaCl), seedling vigor
and stress tolerance indices dropped steadily (Figure E,F). Similarly, differing levels of NaCl
have been shown to have a negative/reducing influence on seedling
germination, vigor indices, and growth parameters of a leguminous
plant Vigna radiata.[31] Furthermore, Cucurbita pepo (L.) seeds treated with NaCl had reduced germination, vigor indices,
biological features, and dry biomass.[32] During the process of seed germination, ROS are produced by plasma
membrane-bound peroxisomes, glyoxisomes, and NADPH oxidases.[33] The increased ROS levels impair the cellular
lipids, proteins, and nucleic acids. As a result, seed germination
may be possible only if ROS production is properly regulated.[34] The first step in the germination process is
to hydrate the stored ingredients. Following hydration, the process
of water intake activates metabolic activities, resulting in the leakage
of solutes.[35] The osmotic components of
salinity have a considerable detrimental impact on the hydration of
the embryo, cotyledon, and endosperm.[36]
Figure 1
Effect
of increasing NaCl concentrations on germination attributes
and seedling parameters of peas germinated on soft agar plates treated
with 0, 2, 50, 100, 150, 200, and 400 mM NaCl; percentage seed germination
(A), plumule length (B), radicle length (C), dry weight (D), seedling
vigor index (E), and mean seedling length (F). Each value is a mean
of three replicates. Mean values followed by different letters are
significantly different at p ≤ 0.05 according
to Duncan’s multiple range (DMRT) test. Vertical bars represent
means ± SD (n = 3), and error bars represent
standard deviation (SD).
Effect
of increasing NaCl concentrations on germination attributes
and seedling parameters of peas germinated on soft agar plates treated
with 0, 2, 50, 100, 150, 200, and 400 mM NaCl; percentage seed germination
(A), plumule length (B), radicle length (C), dry weight (D), seedling
vigor index (E), and mean seedling length (F). Each value is a mean
of three replicates. Mean values followed by different letters are
significantly different at p ≤ 0.05 according
to Duncan’s multiple range (DMRT) test. Vertical bars represent
means ± SD (n = 3), and error bars represent
standard deviation (SD).The seed reserves are
engaged in the turnover and de novo synthesis
of macromolecules, as well as embryonic development and elongation.[37] Many studies have shown that increasing salt
stress causes seed germination to be delayed and the percentage of
germination to be reduced. The delayed seed germination and a considerable
decrease in percent germination due to the exposure to salinity-induced
stress are reported.[38] Furthermore, at
quantities above the species’ tolerance threshold, salt can
completely impede seed germination.[39]
NaCl Reduced the Morphological Features (Growth and Dry Biomass)
of Peas
The process of seed germination involves physiological,
metabolic, and molecular mechanisms that are required for the expansion
of the embryonic axis. The fundamental components of a plant’s
life cycle are seedling germination and establishment. Plant density,
homogeneity, and management options in crop production are all influenced
by seedling establishment.[35] Germination
can often be influenced by a variety of abiotic stress elements including
salinity, drought, heavy metals, etc.[38]All of the growth characteristics investigated were influenced
by the presence of NaCl in the rooting medium, and the high NaCl level
had maximum detrimental effect. For instance, at 200 mM NaCl, germination
rate (in pot soils), root length (RL), and dry weight (DW) of roots
were significantly reduced by 50, 70, and 65%, respectively, compatred
to the untreated control (Figure A–D). Salt has a stifling and reducing impact
on plant growth might possibly be due to (i) decreasing the soil solution’s
osmotic potential surrounding the roots, (ii) increasing the concentrations
of certain ions in tissues that are damaging, and (iii) modifying
the nutrient status of the needed ions for overall physiological processes
of plants. Several researchers have stated that salinity has a negative
impact on crop plants. In this regard, Khator et al.,[40] for example, found that NaCl caused oxidative stress and
biochemical, physiological, and morphological alterations in two legumes.
Similarly, in two varieties of green gram cultivated in various amounts
of NaCl under pot-house conditions, salts had a negative effect on
water relations, ion build-up, and plant nutrients.[41] The reduction/suppression in biological features of plants
under increasing salinity stress may be possibly due to the lower
water potential, ion toxicity, and imbalance excreted by NaCl.
Figure 2
Effect of increasing
NaCl concentrations on biological parameters,
photosynthetic pigments, and enzymatic activity of pea plants raised
in pot soils treated with 0, 2, 50, 100, 150, 200, and 400 mM NaCl;
seed germination (A), plant length (B), dry biomass at 90 DAS (C),
dry biomass at 130 DAS (D), chlorophyll content (E), and nitrate reductase
activity (F). Each value is a mean of three replicates where each
replicate constituted three plants/pots. Mean values followed by different
letters are significantly different at p ≤
0.05 according to the DMRT test. Vertical bars represent means ±
SD (n = 3), and error bars represent SD.
Effect of increasing
NaCl concentrations on biological parameters,
photosynthetic pigments, and enzymatic activity of pea plants raised
in pot soils treated with 0, 2, 50, 100, 150, 200, and 400 mM NaCl;
seed germination (A), plant length (B), dry biomass at 90 DAS (C),
dry biomass at 130 DAS (D), chlorophyll content (E), and nitrate reductase
activity (F). Each value is a mean of three replicates where each
replicate constituted three plants/pots. Mean values followed by different
letters are significantly different at p ≤
0.05 according to the DMRT test. Vertical bars represent means ±
SD (n = 3), and error bars represent SD.
Photosynthetic Attributes and Nitrate Reductase (NR) Activity
under NaCl Stress
Photosynthetic Pigments
As the concentration
of NaCl
increased from 0 to 400 mM, the chlorophyll content in pea leaf was
decreased in a comparable manner and a higher salinity level had the
maximum depressive effect. For instance, 400 mM NaCl caused a maximum
and significant (p ≤ 0.05) reduction of 66,
54, and 48% in chl-a, chl-b, and total chlorophyll content, respectively,
compatred to the control (Figure E). It has also been noted that a decrease in chlorophyll
content is accompanied by an increase in salt concentration. The accumulation
of Na and Cl ions in the leaves could be linked to the reduction of
chlorophyll concentration. The loss of chlorophyll as a result of
salt stress is a common occurrence that results in the disordering
of chlorophyll synthesis and the appearance of chlorosis in plants.[42] Due to the loss of enzymes important for the
production and synthesis of leaf pigments, salt stress has a negative
impact on the photosynthetic apparatus, resulting in decreased synthesis
of carotenoid and chlorophyll.[43] Furthermore,
by boosting the activity of chlorophyll degrading enzyme cholorophyllase,
NaCl stress decreases the chlorophyll molecules of plants, causing
a breakdown of the chloroplast structure and instability of pigment–protein
complexes.[44] Furthermore, the high NaCl
level negatively influences the pigment composition in plant foliage
by (i) suppressing the electron transport (ii) inactivating the reaction
sites in photosystem II (PS-II),[45] (iii)
obstructing the oxygen-evolving complex (OEC) and (iv) destroying
the electron transfer capacity on the donor side of PS-II.[46] In addition, increasing concentrations of sodium
(Na+) and chloride (Cl-) ions in nonstomatal leaf tissues
can also cause a harmful impact on photosynthesis-limiting metabolic
activities.[47]
Nitrate Reductase (NR)
Activity
In higher plants, nitrate
reductase (EC 1.6.6.1) is the first and most important enzyme involved
in the nitrate assimilation pathway. In tissue, its catalytic activity
is complexly regulated in response to many environmental factors.
The post-translational changes of the nitrate reductase protein cause
fast modulation of NR activity by a variety of external stimuli. Because
enzyme nitrate reductase (NR) is sensitive to Na and Cl ions, it is
a good indicator of NaCl-induced toxicity. While measuring the NR
activity in peas, it was observed that with the increasing NaCl concentration
in the rooting media, the activity of NR was steadily dropped in both
young and old pea leaves (Figure F). The detrimental effect of NaCl on NRA was more
evident for salt-sensitive bean plants than for salt-tolerant cotton
plants, according to Gouia et al.[48] The
toxicity of Na and Cl, as well as low nitrate availability, could
explain the inhibition of NRA. Changes in nitrate reductase activity
in response to salinity were associated with an increase in the enzyme’s
activation status in roots and a decrease in the phosphorylated enzyme
pool in the cytosol. Many factors influence how salt affects NR activity
including plant species, nitrogen supply availability, salt content,
and time duration of stress exposure to plants. Like present observation,
exposure to increasing levels of NaCl significantly decreased the
activity of NR in roots and leaf tissues of various agriculturally
important vegetable crops including Solanum lycopersicum L. (tomato), Cucumis sativus L. (cucumber),[49]Zea mays L. (maize),[50]Beta vulgaris L. (sugar beet),[51]V.
radiata L. (green gram),[52]Cicer arietinum L. (chickpea),[53] etc.
Soluble Protein (SP) and
Sugar (SS) under NaCl Stress
The soluble protein concentration
in pea plants was increased considerably
(p < 0.05) when exposed to NaCl. In the absence
of salt (under control), the amount of soluble protein extracted from
pea tissues was 23.4 μg mL–1, which, however,
increased by 65.2 μg mL–1 (64%) at 400 mM
NaCl (Figure A). The
following factor may account for the elevated soluble protein level
generated by NaCl. Salt promotes the production of various primitive
proteins while also increasing the expression of multiple genes. The
findings of this study revealed that plants exposed to salt stress
had higher soluble protein levels than plants exposed to nonsaline
environments. Proteins accumulated in plants cultivated in saline
settings may work as a nitrogen storage form that is reutilized once
the stress has passed, as well as play an osmotic regulatory role.
Osmotic stress is a key method for plants to cope with salt stress,
and it is induced by high salinity levels. It is a critical process
for sustaining the water content of cells by increasing net solute
concentrations or lowering the cell water potential through osmotic
adjustment.[54] The two possible physiological
responses to osmolyte build-up under stress are (i) lowering the cell’s
osmotic potential and (ii) stabilizing the membranes and macromolecular
structure.[55]
Figure 3
Effect of increasing
concentrations (0–400 mM) of NaCl on
soluble protein content (A), soluble sugar (B), Na+ ion
concentration (C), and K+ ion concentration (D) of pea
plants grown under pot-house conditions. Each value is a mean of three
replicates where each replicate constituted three plants/pots. Mean
values followed by different letters are significantly different at p ≤ 0.05 according to the DMRT test. Vertical bars
represent means ± SD (n = 3), and error bars
represent SD.
Effect of increasing
concentrations (0–400 mM) of NaCl on
soluble protein content (A), soluble sugar (B), Na+ ion
concentration (C), and K+ ion concentration (D) of pea
plants grown under pot-house conditions. Each value is a mean of three
replicates where each replicate constituted three plants/pots. Mean
values followed by different letters are significantly different at p ≤ 0.05 according to the DMRT test. Vertical bars
represent means ± SD (n = 3), and error bars
represent SD.Under NaCl stress, soluble proteins
are important for osmotic correction
and can provide a storage form of nitrogen. Sugars that are soluble
in water serve as key osmolytes in maintaining cell homeostasis.[56] Soluble sugars appear to play a protective role
in the membrane as well as osmotic adjustment in the root systems.
Here, with increasing salt concentrations (0–400 mM NaCl),
the quantity of soluble sugar was also increased in plant tissues
(Figure B). Under
NaCl stress, an increase in soluble sugar concentration could be due
to the increased production of certain stress-related proteins.[57] Under NaCl stress, modifications in soluble
sugars are accompanied by changes in CO2 absorption, enzyme
activity, and gene expression.[58] In Nitraria tangutorum, Liu et al.[59] found that saline stress caused an increase in total soluble
sugars and total soluble proteins. When K+ concentration
is low, carbohydrates lead to an increase in osmotic pressure in stomata,
permitting stomatal opening.[60] Likewise,
a remarkable increase in the soluble sugar content in Tagetus minuta (L.) plants was observed when exposed
to 200 mM NaCl concentration.[61]
Effect
of NaCl on Na+ and K+ Ion Concentration
and Relative Leaf Water Content (RLWC) in Peas
When plants
are exposed to salt, sodium ions (Na+) contend with potassium
ions (K+), resulting in nutritional and metabolic disturbance
that ultimately caused the death of plant cells. To address these
difficulties, the amounts of Na+ and K+ in the
leaf tissues of salt-treated pea plants were examined. With increasing
salt concentrations, the build-up of Na+/K+ increased
continuously. At the 400 mM NaCl level, for example, a maximum build-up
of 20.4 and 34.6 mg g–1 fw in Na+ and
K+ concentrations was observed (Figure C,D). A high K+/Na+ ratio is one of the markers of good salt stress defense mechanisms.[62] Also, it is well known that the ability of plants
to withstand salt stress is highly dependent on the condition of their
K+ nutrition.[63] Increased K+ supply in the root environment may help to alleviate the
loss of plant biomass caused by salt.At high salinity levels
(400 mM), peas showed the maximum and considerable reduction (71%)
in RLWC (Figure A).
The accumulation of poisonous ions such as Na+ and Cl–, which reduces the leaf expansion and stomata closure,
resulting in a decrease in intracellular CO2 partial pressure,
which could easily explain these findings.[64] Salinity reduces the capacity of plants to absorb water, resulting
in a quick fall in the growth rate and a plethora of biochemical changes
comparable to those seen during water shortage.[65]
Figure 4
Relative leaf water content (A), proline (B), and MDA content (C)
accumulated in plant tissues detached from pea raised in pot soils
treated with 0, 2, 50, 100, 150, 200, and 400 mM NaCl. Each value
is a mean of three replicates where each replicate constituted three
plants/pots. Mean values followed by different letters are significantly
different at p ≤ 0.05 according to the DMRT
test. Vertical bars represent means ± SD (n =
3), and error bars represent SD.
Relative leaf water content (A), proline (B), and MDA content (C)
accumulated in plant tissues detached from pea raised in pot soils
treated with 0, 2, 50, 100, 150, 200, and 400 mM NaCl. Each value
is a mean of three replicates where each replicate constituted three
plants/pots. Mean values followed by different letters are significantly
different at p ≤ 0.05 according to the DMRT
test. Vertical bars represent means ± SD (n =
3), and error bars represent SD.
NaCl Changed the Proline and Malondialdehyde (MDA) Content in
Peas
To maintain the ionic balance, cytoplasm accumulates
the low molecular mass compounds in the vacuoles because suitable
solutes do not interfere with normal physiological reactions and instead
replace water in biological reactions. The increasing NaCl treatment
generated an increase in proline content in the leaves of the investigated
pea plant. The lower level of salt caused the minimum uptake of proline
in plant tissues which, however, increased at greater NaCl concentrations.
As an example, at 400 mM NaCl, 169 μg proline g–1 fw was accumulated in pea roots, which is 90% higher than that in
the control (Figure C). The ability of the cell to sustain its turgor pressure at low
water potential improves when the osmotic potential is lowered by
osmolyte build-up in response to stress. This appears to be required
for physiological tasks such as photosynthesis, enzyme activity, and
cell expansion. In salt-stressed plants, proline, which is abundant
in higher plants, accumulates in greater quantities than other amino
acids.[66] Under stressful conditions, induction
or activation of proline biosynthesis enzymes, as well as decreased
proline oxidation to glutamate, decreased the proline consumption
in protein synthesis and increased protein turnover, which could all
contribute to proline accumulation.[67] Osmotic
and salinity stresses regulate the expression of genes encoding important
enzymes for proline synthesis (P5C synthase; EC 2.7.2.11, P5C reductase;
EC 1.5.1.2) and proline oxidation (proline dehydrogenase; EC 1.4.3),
which leads to an increase or a decrease in proline concentration
in plant tissue.[68] During early poststress
metabolism, proline appears to be the predominant source of energy
and nitrogen, and proline accumulation appears to supply energy for
growth and survival, resulting in salinity or alkalinity tolerance.
Proline synthesis and accumulation generated by salt may have worked
as a compatible solute, allowing plant tissues to survive stress,
according to the research. Like the current finding, various researchers
have reported the salinity-induced increase in the concentration of
proline. For example, the increasing NaCl treatment significantly
increased the proline content in Brassica juncea (L.) plants.[69]The production of
malondialdehyde (MDA) is often utilized as a broad measure of the
degree of lipid peroxidation caused by oxidative stress. Salt stress
can cause oxidative stress, which can lead to the formation of lipid
peroxidation products such as MDA. Like other stressor molecules (proline),
the content of MDA in the roots and leaves tissues of pea plants under
NaCl stress increased with increasing concentrations of salt, indicating
cumulative damage (Figure D). The findings presented are in line with previous studies.[70] The increased quantity in malondialdehyde, as
well as O2– and H2O2 levels, suggested that NaCl promoted oxidative stress in plant organs
of pea. It is believed that the contents of O2– and H2O2 increased first and subsequently
declined in the root, while they always increased in the leaves, as
revealed by studying the tendency of O2– and H2O2. Because roots are the earliest and
most vulnerable plant organ to be exposed to contaminants and pressures.
As a result, physiological and metabolic abnormalities, as well as
toxic symptoms, first manifested themselves in the roots. Similar
to this, increased salinity stress adversely affected the Portulaca oleracea (L.) plants where the amounts
of proline and MDA significantly increased with increasing NaCl concentrations.[71] The increase in the quantity of proline and
MDA in pea plants under saline conditions suggested that increasing
salinity increased organic matter’s contribution to osmotic
adjustment. Plants respond to soil salinity by adjusting their osmotic
balance, which is a critical component of their physiological system.[72]
NaCl Modulated Antioxidant Enzymatic Activity
in Peas
In response to injury, plants have efficient scavenging
systems.[20] By stabilizing the ROS levels
in plants, the
antioxidant enzymatic system protects the plant cells.[73] Superoxide dismutase (SOD) is the cell’s
first line of defense against ROS since the superoxide radical is
a precursor to a variety of other highly reactive species, so maintaining
a stable state of superoxide concentration via SOD is a crucial defensive
mechanism.[74] Under stressful situations,
peroxidase (POD) activity reflects the changes in cell wall mechanical
characteristics and cell membrane integrity in plant leaves.[75] Catalase (CAT) is the most widely distributed
oxidoreductase, converting H2O2 to O2 and H2O.[76] An adapted ROS-scavenging
system including CAT, POD, SOD, ascorbate peroxidase (APX), and glutathione
reductase (GR) might provide some protection from oxidative damage
under salt-stressed circumstances.[77] With
increasing NaCl concentrations, the antioxidant enzymatic activities
in root and leaf tissues of pea plants were progressively increased.
As an example, APX, CAT, POD and SOD activities in root tissues were
maximally increased by 68, 80, 74, and 58%, respectively, at 400 mM
NaCl with respect to untreated control plants (Figure A–D). Further, it has been noted that
under salinity stress, root tissues of peas accumulated more antioxidants
compared to leaf tissues. In this case, taking an example of CAT activity,
at 400 mM NaCl, root tissues had 7.1 mg g–1 fw,
while, 3.56 mg g–1 fw was recorded for leaf tissues.
The higher antioxidant levels indicate that they are actively involved
in scavenging ROS generated by NaCl toxicity, implying that the plants
have a high ability to withstand salt stress due to the well-functioning
antioxidant defensive mechanism. Furthermore, NaCl had a more pronounced
effect on the root system as the quantities of CAT and POD were larger
in roots than in leaves, which can be explained by the fact that NaCl
comes into direct contact with the roots and is largely absorbed via
the root system. Only a limited percentage of high-concentration NaCl
stored in roots makes it to the leaves. As a result, roots are subjected
to more oxidative stress than leaves. Salinity-induced increases in
antioxidant enzyme activity may protect the biological molecules of
studied pea plants from O2-induced damage.[78] Also, this improvement would have aided in the removal
of ROS from pea seedlings. The build-up of antioxidant enzymes in
some species under stress conditions is attributable to their tolerance
ability, which is not the same in all plant species.[79] Salinity stress boosted the antioxidant enzymes such as
polyphenol oxidase (PPO), catalase, and superoxide dismutase (SOD)
in Sesuvium portulacastrum L.[80]
Figure 5
Antioxidative defense enzymes; ascorbate peroxidase (APX)
(A),
catalase (CAT) (B), peroxidase (POD) (C) and superoxide dismutase
(SOD) (D) extracted from root and leaf tissues of pea plants detached
from pot soils treated with 0, 2, 50, 100, 150, 200, and 400 mM NaCl.
Each value is a mean of three replicates where each replicate constituted
three plants/pots. Mean values followed by different letters are significantly
different at p ≤ 0.05 according to the DMRT
test. Vertical bars represent means ± SD (n =
3), and error bars represent SD.
Antioxidative defense enzymes; ascorbate peroxidase (APX)
(A),
catalase (CAT) (B), peroxidase (POD) (C) and superoxide dismutase
(SOD) (D) extracted from root and leaf tissues of pea plants detached
from pot soils treated with 0, 2, 50, 100, 150, 200, and 400 mM NaCl.
Each value is a mean of three replicates where each replicate constituted
three plants/pots. Mean values followed by different letters are significantly
different at p ≤ 0.05 according to the DMRT
test. Vertical bars represent means ± SD (n =
3), and error bars represent SD.
NaCl-Induced Cell Damage and ROS Generation in Pea Roots
To study the salinity-induced oxidative damage, roots of pea plants
were exposed to 0–400 mM NaCl. Further, cell damage and ROS
production in salinity stressed plant samples, roots were stained
with propidium iodide (PI) and 3,3′-diaminobenzidine (DAB)
and dichloro-dihydro-fluorescein diacetate (DCFH-DA), respectively.
Increasing red fluorescence in roots is a sign of cellular damage.
It is very complicated to assess the fluorescence in control roots
(since these dyes are only taken up by dead tissues/cells) (Figure A–D). The
confocal microscopy images revealed that varying NaCl levels showed
variable patterns of fluorescence intensity. The lower level (50 mM)
of fluorescence intensity showed that minimum concentrations of salts
can also induce cellular damage. With an increase in salt concentrations,
the intensity of red fluorescence increased considerably. Being a
fluorescent chemical/intercalating agent, PI is very often applied
to stain DNA molecules and can be utilized as an alternate agent to
evaluate cell membrane damage.[81] Damage
to the cell membrane integrity caused morphological alteration in
cells. PI staining results corroborated the damaging effect of salinity-induced
stress on the cell membrane in pea root tips. The cells exposed to
100 mM NaCl had lower fluorescence intensity, indicating that lower
levels of salts can also cause cell damage. With higher NaCl concentrations
and longer treatment times, the harmful impact became more pronounced.
When salt stress is temporary or adjustable at the seedling stage,
nucleotides could be produced by DNA breakdown and reallocated for
shoots and new root formations. Here, salinity stress resulted in
cell death. Also, the growth of roots may be hampered as a result
of this cell loss. Similar to this observation, a salinity-induced
increase in ROS production in root tissues of rice cultivars has been
reported.[82] Likewise, Li et al.[83] have also observed that higher concentrations
of NaCl induced the induction of antioxidant enzymes and increased
ROS production in meristematic root tips of Oryza sativa (L.).
Figure 6
(A–D) CLSM images showing the cellular damage in root tissues
of peas exposed to different concentrations of NaCl as revealed by
increased PI fluorescence (left to right: roots treated with 0, 50,
100, and 400 mM NaCl, respectively). (E–H) Reactive oxygen
species (ROS) generation in roots of pea plants treated with increasing
salt levels as revealed by staining with 3,3′-diaminobenzidine
(DAB) and 2′,7′-dichlorodihydrofluorescein diacetate
(DCFH-DA) treatment (left to right: roots treated with 0, 50, 100
and 400 mM NaCl, respectively). (I, J) Quantification of dose-dependant
increase in cell damage and ROS generation. Each value is a mean of
three replicates where each replicate constituted three plants/pots.
Mean values followed by different letters are significantly different
at p ≤ 0.05 according to the DMRT test. Vertical
bars represent means ± SD (n = 3), and error
bars represent SD.
(A–D) CLSM images showing the cellular damage in root tissues
of peas exposed to different concentrations of NaCl as revealed by
increased PI fluorescence (left to right: roots treated with 0, 50,
100, and 400 mM NaCl, respectively). (E–H) Reactive oxygen
species (ROS) generation in roots of pea plants treated with increasing
salt levels as revealed by staining with 3,3′-diaminobenzidine
(DAB) and 2′,7′-dichlorodihydrofluorescein diacetate
(DCFH-DA) treatment (left to right: roots treated with 0, 50, 100
and 400 mM NaCl, respectively). (I, J) Quantification of dose-dependant
increase in cell damage and ROS generation. Each value is a mean of
three replicates where each replicate constituted three plants/pots.
Mean values followed by different letters are significantly different
at p ≤ 0.05 according to the DMRT test. Vertical
bars represent means ± SD (n = 3), and error
bars represent SD.Plants go through a number
of stress acclimation processes, including
gene regulation in oxidative stress responses, which results in stimulation
of antioxidant enzymes, to protect cells from excessive accumulation
of reactive oxygen species caused by numerous environmental stresses.
When a cell is under stress, distinct forms of ROS are produced in
different compartments. The activation of antioxidant enzyme genes
in response to oxidative stress is an important indicator for further
research into plant antioxidant defense systems. The effect of increasing
salt levels on ROS production in pea roots was qualitatively examined
using in vivo histochemical labeling with fluorescent dyes. When root
tissues were subjected to increasing NaCl concentrations, staining
with 3,3′-diaminobenzidine (DAB) and treatment with dichloro-dihydro-fluorescein
diacetate (DCFH-DA) demonstrated an increase in ROS formation (in
the form of an increase in green color), with increased ROS generation
in the root tip region, compared to untreated controls (Figure E–H). Salinity-induced
oxidative stress in different plant species has been reported. For
example, NaCl caused oxidative stress by increasing the accumulation
of hydrogen peroxide in Triticum aestivum (wheat) seedlings, which was observed after staining the root tissues
with fluorescent probe DCFH-DA.[84] In a
study, Hernandez et al.[85] examined the
accumulation of hydrogen peroxide in the roots tissues of Brassica oleracea (L.) exposed to long- and short-term
NaCl stress. The increase in fluorescence of DCFH-DA-stained roots
indicated that light appears to reside in the cytoplasm and apoplast
of root tip cells. Also, H2O2 appears to be
mostly found in the mitochondrial cristae and external membrane.
NaCl-Induced ROS Generation, Superoxide Ion (O2–), and Hydrogen Peroxide (H2O2) Content in
Pea Organs
In the presence of NaCl stress,
reactive oxygen species (ROS) including −OH (hydroxyl radicals),
O2–, and H2O2 are
increased.[17] ROS interact with other biological
components, causing oxidative damage such as lipid peroxidation, protein
degradation, and DNA damage.[86] The current
study found that salt treatment increased the O2– and H2O2 contents of peas, which was related
to the decreased integrity of the plasma membrane in plants. Plant
plasma membranes are thought to be the first biological structures
to be impacted by the toxicity of environmental stressors including
salts.[87] ROS can affect the biomolecules
and cause cell membrane lipid peroxidation. As a result of the damage
to cell membranes, the selectivity of cell membranes has diminished.Considering these, the impact of increasing salts on superoxide
anion (O2–) and hydrogen peroxide (H2O2) concentrations in leaf and root tissues of
pea plants was observed. The amounts of superoxide anions in both
the plant organs were upsurged significantly (p ≤
0.05) with increasing NaCl treatments. The O2– content reached the maximum level at 400 mM NaCl. Similarly, salt-induced
production of H2O2 in root and leaf tissues
of peas varied with different NaCl concentrations. A similar trend
was recorded for hydrogen peroxide, i.e., as the level of NaCl increased,
the production of H2O2 was also increased and
high NaCl levels caused the maximum production. At 400 mM NaCl, the
H2O2 contents in root and leaf tissues of peas
were maximally increased by 75 and 83%, respectively, when compared
to the untreated control (Figure A,B). Similar to our observation, different levels
of salts significantly induced the production of oxidative stress
(H2O2, O2–.) on
rapeseed (Brassica napus L.) cultivars.[88] Additionally, Hernández et al.[89] found an exceptionally high increase in apoplastic
hydrogen peroxide (H2O2) content and O2– production in NaCl-treated pea leaves that caused
necrotic lesions.
Figure 7
Effect of increasing NaCl concentrations on ROS content
in pea
plants raised in pot soils treated with 0, 2, 50, 100, 150, 200, and
400 mM NaCl; O2– content (A) and H2O2 content (B). Each value is a mean of three replicates
where each replicate constituted three plants/pots. Mean values followed
by different letters are significantly different at p ≤ 0.05 according to the DMRT test. Vertical bars represent
means ± SD (n = 3), and error bars represent
SD.
Effect of increasing NaCl concentrations on ROS content
in pea
plants raised in pot soils treated with 0, 2, 50, 100, 150, 200, and
400 mM NaCl; O2– content (A) and H2O2 content (B). Each value is a mean of three replicates
where each replicate constituted three plants/pots. Mean values followed
by different letters are significantly different at p ≤ 0.05 according to the DMRT test. Vertical bars represent
means ± SD (n = 3), and error bars represent
SD.
Conclusions
Plants
have evolved various strategies to reduce the damage caused
by nonessential high NaCl exposure. When the concentration of NaCl
inside the cells becomes too high, a defense mechanism kicks in to
protect the cells from oxidative stress, which can cause cell death
as well as stress-induced adaptation and survival. In the current
findings, as the level of salinity increased, the number of damaged
and dead cells in plant tissues also increased. The growth of pea
root severely slowed down, which could be attributed to the death
of large root cells as a result of the high NaCl concentration and
prolonged NaCl exposure. In addition, the ROS levels significantly
increased with an increase in NaCl concentration. Hence, when the
level of ROS excessively increased, the plant cell membrane system
was injured, resulting in changes in MDA and osmotic regulatory chemicals.
Significant changes in antioxidant enzymatic activities, lipid peroxidation,
and cell damage have been observed in peas, and they can be used as
biomarkers to determine the extent of damage in plants caused by NaCl.
Conclusively, the information gathered here could be useful in deciphering
the tolerance mechanism in agriculturally important edible crops under
NaCl-stressed conditions.
Experimenal Section
Assessment of Seedling
Germination Attributes of Peas in the
Presence of NaCl Stress
P. sativum seeds were sterilized for 1 min in a 0.5% sodium hypochlorite (NaOCl)
solution. After that, distilled water was used to wash them twice.
In Petri dishes (9 cm), 10 mL of the test solution was added to one
disc of Whatman No. 1 filter paper. Parafilm was used to prevent evaporation
on the dishes. The germination experiment was carried out in incubators
at 25/15 °C for 20 days in four repetitions with 25 seeds in
each treatment under a 12 h light/12 h dark photoperiod. The seedlings
grew in 50, 100, 200, 300, and 500 mM NaCl, as well as pure water.
Seeds were counted every day, and when the radicle appeared, they
were judged to have germinated and removed from the Petri dishes.
Salt Treatment and Culturing of Pea
Seeds of P. sativum (L.) variety (var. Arkil) were purchased
from the local seed market. Seeds were washed, rinsed, and desiccated
at room temperature after being disinfected/sterilized using NaOCl
(2%). The pot experiment was conducted in a pot-house condition. The
solution of sodium chloride (NaCl) was produced in double-distilled
water (DDW) at concentrations of 0, 50, 100, 200, and 400 mM and applied
as a presowing application to moisten the soil (7.6 pH value, EC =
0.863 mv cm–2, % (organic carbon) OC = 5.17 g kg–1, total nitrogen (N) = 0.76 g kg–1, total P = 12.3 mg kg–1, K = 14.08 mg kg–1, Mg = 13.01 mg kg–1, water holding capacity (mL
g–1) = 0.512, calcium (mg kg–1) = 10.15, sodium (mg kg–1) = 7.61, carbonate (mg
kg–1) = 22.9, bicarbonate (mg kg–1) = 10.7, cation exchange capacity (cmol kg–1)
= 14.2, anion exchange capacity (cmol kg–1) = 5.7)
at least 1 day prior to sowing (20 cm in length and 24 cm in diameter)
containing 5 kg of unsterilized soil. Each test concentration was
repeated three times, and the pots were placed in a fully random block
configuration. Seedlings were thinned after germination, and 15 days
following emergence, two uniform healthy pea seedlings were kept in
each pot. Pots were irrigated on a regular basis and kept in open
field conditions. The crop was harvested at two different stages:
90 and 130 days after sowing (DAS). The whole study was performed
for 2 successive years, and each individual experiment with identical/similar
treatment was repeated for 2 consecutive years to validate the reproducibility
and accuracy of data.
Effect of NaCl on Seed Germination and Biological
Features (Length
and Dry Biomass) of Peas
The NaCl-treated pea plants were
harvested at 90 and 130 DAS, and morphological parameters like the
length of plant organs (root and shoot), fresh weight, and dry biomass
were measured. Plant samples were dried in an oven at 80 °C for
2 days and then weighed to determine dry biomass.
Estimation
of Chlorophyll Content and Nitrate Reductase Activity
The
accumulation of leaf photosynthetic molecules (chlorophyll
and carotenoid) in NaCl-treated and untreated pea plants was estimated
following the methods previously described by Arnon[90] and Kirk and Allen.[91]
Nitrate
Reductase (NR) Activity
The activity of nitrate
reductase (NR; EC 1.6.6.1) was determined using the intact tissue
technique as previously described by Siddiqui et al.[92] The freshly detached NaCl-treated leaf samples were incubated
in a solution comprising 2.5 mL of phosphate buffer (pH 7.5), 0.2
M potassium nitrate, and 5% iso-propanol. The reaction was calorimetrically
determined by adding 1% sulfanilamide and 0.2% N-1-naphthylethylene-diamine
di-hydrochloride. A calibration curve was used to compare absorbance
measurements taken at 540 nm. Nanomoles NO2/g per FW (fresh
weight) per hour were used to measure NR activity.
Determination
of Soluble Protein (SP) and Soluble Sugar (SS)
Contents
In this study, the soluble protein concentration
was determined by means of Bradford’s[93] technique using a reference solution of bovine serum albumin (BSA).
At the end of each time interval (7 days) of the NaCl treatment, the
fresh roots and leaves from each treatment (six seedlings) were rinsed
in distilled water, dried, and placed in a mortar with 5 mL 0.05 M
PBS (pH 7.8). The homogenate was centrifuged at 10 000g (for 20 min), and the supernatant was utilized to determine
the soluble protein level. The amount of soluble protein per g of
fresh weight was calculated.
Determination of Leaf Relative Water Content
(LRWC) and Na+ and K+ Concentrations
The salt-treated
leaf samples were cut, weighed, and stored in DDW for 3 h to get the
turgid weight for the measurement of the relative leaf water content
(RLWC). After that, the samples were oven-dried for 24 h at 80 °C
until they reached a constant weight.[94] The RLWC was calculated using the following formulaLeaf powder was homogenized and transferred
to Erlenmeyer flasks in six different treatments. A 6.0 mL solution
of nitric acid (HNO3) + perchloric acid (HClO4) was added to this mixture. After that, the samples were digested
in a water bath (at 40 °C) until the volume of the sample was
decreased to 1.0 mL. The residual volume was brought up to 100 mL
with DDW after digestion. The concentrations of Na+ and
K+ were calculated in the sample.[95]
Proline and MDA Content Estimation
For determination
of stress, biomarker, i.e., proline content accumulated in peas plants
raised in soil amended with elevated level of salts was used.[96] Further, for estimation of the malondealedehyde
(lipid peroxidation) content, the freshly detached roots and leaves
(500 mg) were homogenized using a prechilled mortar and pestle with
10 mL of 5% (w/v) trichloroacetic acid (TCA; C2HCl3O2) (SRL Pvt. Ltd. India) and centrifuged at 12 000g for 20 min at 4 °C. The supernatant (2.0 mL) was
added to a tube containing 2.0 mL of 0.67% (w/v) thiobarbituric acid
(TBA; C4H4N2O2S) (Hi-media,
Pvt. Ltd. India). Then, the tubes were heated in a water bath at 100
°C for 30 min and rapidly cooled to 4 °C in an ice bath
to terminate the reaction, and afterward, the reaction mixture was
centrifuged at 10 000g for 10 min at 4 °C.
The absorbance of the supernatant was measured at 532, 600, and 450
nm. The MDA content was calculated using the extinction coefficient
of 155 mM–1 cm–1.[97]
Antioxidant
Enzyme Estimation in NaCl-Treated Peas
For the estimation
of the antioxidant enzymatic activity in pea plants,
0.5 g of freshly detached roots and leaves of NaCl-treated plants
was homogenized in 50 mM phosphate buffer having a pH value of 7.8
under cold conditions after being pulverized with a mortar and pestle.
The homogenized mixture was centrifuged at 12 000g for 10 min at 4 °C after being filtered through four layers
of muslin cloth. Then, the prepared samples were used for the analysis
of ascorbate peroxidase (APX; 1.11.1.11), catalase (CAT; 1.11.1.6),
and guaiacol peroxidase (GPX, EC 1.11.1.7) activities (refer to the Supporting Information for detailed descriptions).
Assessment of NaCl-Induced Cell Damage and ROS Generation
Root Staining
with Propidium Iodide (PI)
The undamaged
root tips of peas strained by NaCl were subjected to various doses
of NaCl to investigate the cellular damage in root tip cells of peas
affected by NaCl (0–400 mM). For the assessment, root samples
were stained in the dark at room temperature with propidium iodide
(PI) and then rinsed three times with sodium phosphate buffer (PBS)
for 3 min each time (pH 7.8).[98] Using the
analysis and measure feature of ImageJ software, the fluorescence
density of ten undamaged root tips of peas under NaCl stress was evaluated
to study the distribution (NIH, Bethesda, MD). A confocal laser scanning
microscope with an excitation maximum at 535 nm and a fluorescence
emission maximum at 617 nm was used to analyze the immunofluorescent
specimens.
Determination of O2– and H2O2 Concentrations
To determine
the concentration
of ROS generation in NaCl-treated pea tissues, the previously used
method of Velikova et al.[99] was applied.
To determine the hydrogen peroxide (H2O2) content
in NaCl-exposed peas, 500 mg of plant samples (roots and leaves) was
homogenized (experiment conducted in an ice bath) in 5.0 mL of acetone
solution. Thereafter, the mixture solution was centrifuged (at 10 000g for 20 min at 4 °C). From this extract, 1.0 mL was
taken and mixed with 0.20 mL of titanium sulfate (TiO(SO4); 5%) and 0.2 mL of ammonia. The mixture solution was centrifuged
at 10 000g for 20 min at 4 °C after it
had precipitated. After rinsing three times with acetone, 5.0 mL of
2.0 M H2SO4 (sulfuric acid) was added. The absorbance
of the solution was read at 415 nm until the sediments dissolved,
and the H2O2 content was determined using a
reference curve.According to Sun et al.,[100] the rate of O2– generation
was evaluated by measuring the generation of nitrite from hydroxylamine
in the presence of O2–. For the assay,
0.2 g of frozen leaves (in an ice bath) was extracted with 2.0 mL
of 50 mM PBS (pH 7.8). The centrifugation of this mixture was done
at 12 000g (for 20 min at 4 °C), thereafter,
0.5 mL supernatant was mixed with 0.5 mL of 50 mM PBS (pH 7.8) and
1.0 mL of 1 mM hydroxylamine hydrochloride (HONH2·HCl).
After 20 min in a water bath at 25 °C, 1 mL of sulfaniclic acid
(C6H7NO3S; 17 mM) and 1 mL of 1-aminonaphthalene
(C10H9N; 7.0 mM) were added to the mixture.
After that, the solution was centrifuged for 3 min at 12 000g at 25 °C after being incubated for 20 min in a water
bath at 25 °C. The absorbance of the supernatant was measured
at 530 nm, and the amount of O2– in the
sample was determined using the standard curve.
Statistical
Analysis
To analyze the data statistically,
each plant treatment was repeated three times. The data was analyzed
using SPSS and Sigma Plot 10.0 software. To evaluate the significance
at p ≤ 0.05, one-way analysis of variance
(ANOVA) and Student’s t-test were utilized
in the statistical study.
Authors: Werner C Antunes; Nicholas J Provart; Thomas C R Williams; Marcelo E Loureiro Journal: Plant Cell Environ Date: 2011-11-23 Impact factor: 7.228