expression of the atnhx1 gene in peanut to increase …
TRANSCRIPT
EXPRESSION OF THE AtNHX1 GENE IN PEANUT TO INCREASE SALT
TOLERANCE IN PEANUT PLANTS
by
MANOJ BANJARA, B.Tech.
A THESIS
IN
BIOLOGY
Submitted to the Graduate Faculty of Texas Tech University in Partial Fulfillment of the
Requirements for the Degree of
MASTER OF SCIENCE
Approved
Hong Zhang
Chairperson of the Committee
Megha N. Parajulee
Paxton Payton
Accepted
Fred Hartmeister
Dean of the Graduate School
August, 2010
©, Manoj Banjara, 2010
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ACKNOWLEDGEMENTS
This thesis would not have been possible without Dr. Hong Zhang's bringing me
into his laboratory. In addition to his philosophical guidance, unlimited encouragement,
and support from the initial to the final level on my research project, his contribution to
research and teaching encourage me to dedicate to science. I would also like to express
my gratitude to my committee members, Drs. Megha N. Parajulee and Paxton Payton
for their valuable help, suggestions, and time. I am indebted to Dr. Parajulee for
introducing me to Dr. Zhang and for his relentless support.
I offer my sincere gratitude to Dr. Guoxin Shen, Dr. Longfu Zhu, Sundaram
Kuppu, Yinfeng Zhu, Rongbin Hu, Jian Chen, Qiang Gu, Hua Qin, Pei Hou, and
Xiaoyun Qiu in Dr. Zhang’s lab for persistent help in experimental design and
management, and for letting me take part in scientific discussions. In addition, I am
grateful to my friends and colleagues in Dr. Rock, Dr. Xie, and Dr. Holaday’s
laboratories.
Lastly, and most importantly, I owe my deepest gratitude to my entire family
residing in US and in Nepal for their firm support, constant encouragement, and
guidance. Without the support from my family members, I would not be able to aspire to
get education in United States.
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TABLE OF CONTENTS
ACKNOWLEDGEMENTS ................................................................................................ ii
ABSTRACT ....................................................................................................................... vi
LIST OF FIGURES ......................................................................................................... viii
LIST OF ABBREVIATIONS ............................................................................................ ix
CHAPTER
I. INTRODUCTION ............................................................................................................1
1.1. Overview ...........................................................................................................1
1.2. The adverse effects of salinity stress ................................................................4
1.2.1. Effects of salinity on plant growth .....................................................4
1.2.2. Effects of salinity on water relations .................................................5
1.2.3. Effects of salinity on leaf anatomy and chloroplast ultrastructure ....6
1.2.4. Effects of salinity on photosynthesis, and photosynthetic pigments
and proteins .......................................................................................7
1.2.5. Effects of salinity on lipids ................................................................9
1.2.6. Effects of salinity on ion levels ........................................................10
1.2.7. Effects of salinity on antioxidative enzymes and antioxidants ........10
1.2.8. Effects of salinity on nitrogen metabolism ......................................11
1.2.9. Effects of salinity on malate metabolism .........................................12
1.3. Mechanisms of plant salt stress tolerance .......................................................13
1.3.1. Sodium compartmentalization into vacuoles ...................................14
1.3.2. Sodium extrusion via the plasma membrane ...................................15
1.3.3. Synthesis or accumulation of osmoprotectants ................................17
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1.3.4. Induction of antioxidative enzymes .................................................18
1.3.5. Induction of plant hormones ............................................................19
1.3.6. Change in photosynthetic pathway ..................................................20
1.4. Characteristics of sodium/proton antiporter ...................................................20
1.5. Strategy to make salt tolerant plants ...........................................................22
1.6. Basis for creating transgenic peanut with higher salt stress tolerance .........24
II. MATERIALS AND METHODS ..................................................................................27
2.1. Vector construction and peanut transformation ............................................27
2.2. Isolation of genomic DNA and PCR analysis of putative transformants .......29
2.3. Isolation of total RNAs and RNA blot analysis ..............................................30
2.4. Salt treatment .................................................................................................32
2.5. Plant growth and biomass measurement under salt treatment in greenhouse 33
2.6. Gas-exchange measurements ..........................................................................33
2.7. Total chlorophyll measurement ......................................................................34
2.8. Statistical analysis ...........................................................................................34
III. RESULTS ....................................................................................................................37
3.1. Creation of AtNHX1-expressing peanut ..........................................................37
3.2. Molecular analyses of AtNHX1-expressing transgenic peanut plants .............38
3.3. AtNHX1-expressing peanut plants are more salt tolerant ...............................41
3.4. AtNHX1-expressing peanut plants demonstrate higher gas exchange
parameters and biochemical parameters for photosynthesis than wild-type
plants under salinity conditions ......................................................................47
IV. DISCUSSION ..............................................................................................................54
4.1. Challenges of Agrobacerium-mediated transformation in peanut ..................57
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REFERENCES ..................................................................................................................59
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ABSTRACT
Salinity and drought are two major environmental stresses that affect agricultural
productivity. To meet the food demand of an increasing population and a warming
environment, the need to generate salt and drought tolerant crops is apparent. High
salinity in the soil makes it harder for plant roots to extract water, and high concentration
of salts within plant cells can be toxic to the cellular enzymes. One approach to improve
salt tolerance in crops is to sequester excess sodium ion (Na+) into the large intracellular
vacuoles via the tonoplast membrane. Consequently, there is reduction of Na+ in
cytoplasm with the accumulation of compatible solutes that restore the correct osmolarity
to the intracellular milieu, which favors water uptake by plant root cells and improves
water retention in tissues under high soil salinity. This approach was successfully
demonstrated in several plants, where overexpression of the Arabidopsis gene AtNHX1
that encodes a vacuolar sodium/proton (Na+/H
+) antiporter resulted in a higher salt
tolerance phenotype.
Peanut (Arachis hypogaea L.) is an important crop of tropical and sub-tropical
regions of the world. To improve yield and quality under salinity stress conditions, the
Arabidopsis gene AtNHX1 was introduced into peanut through Agrobacterium-mediated
transformation. The AtNHX1-expressing peanut plants produced more biomass when
grown on up to 150 mM NaCl in greenhouse conditions. The increased growth of
AtNHX1-expressing peanut plants is likely due to the consequence of higher
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photosynthetic rates in the transgenic plants compared to wild-type plants under saline
conditions. The better performance of AtNHX1-expressing peanut lines compared to
wild-type plants under high salinity indicates that AtNHX1 can be used to enhance salt
tolerance in peanut.
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LIST OF FIGURES
1.1. Model for Na+ regulation in plant cell ...................................................................26
2.1. AtNHX1-overexpression construct used for peanut transformation.......................36
3.1. Analysis of putative AtNHX1-expressing peanut plants by PCR...........................39
3.2. Northern blot analysis of wild-type and AtNHX1-expressing peanut plants .........40
3.3. Phenotypes of wild-type and AtNHX1-expressing peanut plants after
150 mM NaCl treatment ........................................................................................43
3.4. Fresh biomass of wild-type and AtNHX1-expressing peanut plants after
150 mM NaCl treatment ........................................................................................44
3.5. Dry biomass of wild-type and AtNHX1-expressing peanut plants after
150 mM NaCl treatment ........................................................................................45
3.6. Relative amount of chlorophyll present in wild-type and AtNHX1-
expressing peanut plants after 150 mM NaCl treatment ........................................46
3.7. Gas-exchange performance of wild-type and AtNHX1-expressing peanut
plants after 150 mM NaCl treatment .....................................................................49
3.8. Estimation of photosynthetic parameters for wild-type and AtNHX1-
expressing peanut plants after 150 mM NaCl treatment ........................................52
3.9. Estimation of photosynthetic characteristics for wild-type and AtNHX1-
expressing peanut plants after 150 mM NaCl treatment ........................................53
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LIST OF ABBREVIATIONS
APX Ascorbate peroxidase
AtNHX1 Arabidopsis thaliana Na+/H
+ antiporter
ATPase H+
-adenosine triphosphatase
AVP1 Arabidopsis thaliana vacuolar H+-pyrophosphatase
BSA Bovine serum albumin
CAM Crassulacean acid metabolism
CAT Catalase
CO2 Carbon dioxide
DEPC Diethyl pyrocarbonate
EDTA Ethylenediaminetetracetic acid
GB Glycine betaine
GFP Green fluorescence protein
GR Glutathione reductase
ICDH Isocitrate dehydrogenase
IRGA Infra-red gas analyzer
LB Luria-Bertani
MDH Malate dehydrogenase
MOPS 4- morpholinepropanesulfonic acid
MS Murashige and Skoog
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Na+/H
+ Sodium/proton
NaCl Sodium chloride
NADP Nicotinamide adenine dinucleotide phosphate
NHX Na+/H
+ exchanger
NR Nitrate reductase
PCR Polymerase chain reaction
PEG Proton electrochemical gradient
PEPC Phosphoenol pyruvate carboxylase
PPFD Photosynthetic photon flux density
PSII Photosystem II
PPase H+
-pyrophosphatase
RIM Root induction medium
ROS Reactive oxygen species
Rubisco Ribulose -1, 5 -bisphosphate carboxylase/oxygenase
RuBP Ribulose -1, 5 -bisphosphate
SDS Sodium dodecylsulfate
SEM Shoot elongation medium
SIM Shoot initiation medium
SOS Salt overly sensitive
T0 First transgenic plant directly induced from callus
T1 First generation of seeds and plants after self-cross on T0 plants
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TE Buffer solution containing 10 mM Tris and 1 mM EDTA
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CHAPTER I
INTRODUCTION
1.1. Overview
About 20% of the world’s cultivated land and nearly half of all irrigated lands are
unsuitable for growing crops because of contamination with high levels of salt (Rhoades
and Loveday, 1990). More than 800 million hectares of land throughout the world are
salt affected (FAO, 2008). Soil salinity stresses plants in two different ways: high salinity
in the soil makes it harder for roots to extract water, and high concentration of salts
within the plant can be toxic (Munns and Tester, 2008). Salinity stress is one of the most
serious factors limiting the productivity of agricultural crops. Most salt affected land has
arisen from natural causes, from the accumulation of salts over long periods of time in
arid and semiarid zones (Rengasamy, 2002). Repetitive seawater invasion, incorrect
irrigation, and degradation of native saline parent rock are primarily responsible for
increasing soil salinity (Ashraf, 1994). Degradation of native saline rocks releases soluble
salt of various types mainly chlorides of sodium, calcium, and magnesium, and to a lesser
extent, sulfates and carbonates (Szabolcs, 1989). Sodium chloride is the most soluble and
abundant salt released in soil.
Salinity is a soil condition characterized by a high concentration of soluble salts.
The natural floras of highly saline soil are halophytes, which are able to maintain this
exclusion at higher salinities than glycophytes. Sea barley grass, Hordeum marinum, is an
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example that excludes both Na+
and Cl- concentrations up to 450 mM NaCl (Garthwaite
et al., 2005). Since salinity is the common feature of arid and semiarid lands, plants of
this land have evolved mechanisms to tolerate the low soil water potential caused by
salinity as well as by drought, and their ability to tolerate to osmotic stress is a feature of
most glycophytes and halophytes. Salinity induces a change in the signals of root origin,
which changes the hormonal balance of the plant that affects root and shoot growth
(Lerner et al., 1994). Peanut (Arachis hypogaea L.) is a glycophytic plant whose growth
and yield are severely inhibited by high salinity.
Dry weather and irrigation water with high salt concentration are the main factors
that limit the yield of cotton and peanut, which are the major crops in West Texas. The
farmers in the Southwestern USA are constantly facing problems from salinity and
drought. Increasing peanut tolerance against drought and salt stresses would improve its
yield, which will have an enormous impact on the economy of peanut growing states in
America.
Peanut is an economically important legume crop, whose seeds contain 43% oil
and 25% protein. It also has significant impact in tropical and sub-tropical regions of
Asia, Africa, and North and South America (Sharma and Ortiz, 2000). It is the 12th
most
valuable cash crop grown in the United States with a farm value of over one billion US
dollars. American consumers eat more than 6 pounds or 2.7 kilograms of peanut products
each year, which are worth more than $2 billion at the retail level. Texas is ranked second
among the peanut growing states and it accounts for approximately 24% of overall
peanuts grown in the United States. (http://www.peanutsusa.com).
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To improve peanut yield and quality, peanut tolerance to drought and salt
conditions must be enhanced. When Na+ accumulates to high levels in cytosol, it
becomes toxic to enzymes. Excess Na+ in cytosol could be removed by the active
mechanisms into the apoplastic space via plasma membrane or to the large intracellular
vacuole via the tonoplast membrane. In both of these circumstances, there is
accumulation of compatible solutes that restores correct osmolarity in the intracellular
milieu. Sodium ions flow through the Na+/H
+ antiport in the large vacuole membrane-
down to an electrochemical proton gradient generated by two vacuolar proton pumps and
accumulate inside the large intracellular vacuole (Apse et al., 1999).
Engineered transgenic Arabidopsis, tomato, rapeseed, cotton, tobacco, tall fescue,
and Petunia hybrida expressed higher levels of AtNHX1 protein and displayed an
increased vacuolar uptake of Na+ than wild-type plants, which is responsible for
increased salt tolerance (Apse et al., 1999; Zhang and Blumwald, 2001; Zhang et al.,
2001; He et al., 2005; Duan et al., 2009; Tian et al., 2006; Xu et al., 2009). Since the
overexpression of AtNHX1 in native and heterologous systems leads to the same
phenotype, i.e., increased salt tolerance, it suggests that this approach should work in
most plants including peanut. Therefore, this research project is an endeavor to
overexpress the Arabidopsis gene AtNHX1 in peanut to make them more salt tolerant.
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1.2. The adverse effects of salinity stress
Salt suppress the growth of all plants, but the tolerance levels and the growth
retardation at high salt concentrations vary among the species of the plants. Generally,
soil salinity makes it harder for roots to extract water, reducing water potential, causes
ion imblance or disturbaces in ion homeostatis, and also causes ion toxicity, which
inhibits enzymatic functions of key biological processes (Zhang and Blumwald, 2001;
Blumwald et al., 2004; Munns and Tester, 2008). Additionally, secondary stresses, such
as oxidative damage, disrupts cellular homeostasis due to the high ion concentration (Dat
et al., 2000). Growth suppression is directly related to the total soluble salt concentration
or osmotic potential of soil water (Flowers et al., 1977; Greenway and Munns, 1980). All
the major processes such as growth, photosynthesis, protein synthesis, and energy and
lipid metabolism are affected by salt stress. High salinity stress affect various aspects of
crop production.
1.2.1. Effects of salinity on plant growth
The immediate response of plants to salt stress is reduction in the rate of leaf
surface expansion gradually leading to cessation of expansion with the increase in salt
concentration (Wang and Nil, 2000). There is also considerable decrease in the fresh and
dry weights of leaves, stems, and roots (Hernandez et al., 1995; AliDinar et al., 1999;
Chartzoulakis and Klapaki, 2000). High salinity significantly reduces the shoot weight,
plant height, number of leaves per plant, root length, and root surface area per plant in
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tomatoes (Mohammad et al., 1998). Furthermore, increased NaCl results in significantly
decrease root, shoot, and leaf growth biomass and increase in root/shoot ratio in cotton
(Meloni et al., 2001). In Raphanus sativus, total dry weight decreases at higher salinities
and about 80% reduction of growth at high salinity was attributed to the reduction in leaf
area expansion. The small leaf area at high salinity is related to reduced specific leaf area.
The increased tuber/shoot weight ratio is attributed to the tuber formation starting at a
smaller plant size at high salinity (Marcelis and VanHooijdonk, 1999).
1.2.2. Effects of salinity on water relations
Increase in salinity makes water potential and osmotic potential of plants more
negative , whereas increasing salinity increases the turgor pressure (Morales et al., 1998;
Hernandez et al., 1999; Khan et al., 1999; Meloni et al., 2001; Khan, 2001;
Romeroaranda et al., 2001). Short term NaCl stress in jute decreases the relative water
content, leaf water potential, water uptake, transpiration rate, water retention, and water
use efficiency (Chaudhari and Choudhuri, 1997). There is no change in leaf relative water
content, but decrease in leaf water potential and evaporation rate with increased salt
concentration in the halophyte S. salsa (Lu et al., 2002). According to Rajasekaran et al.
(2001), plants under progressive or prolonged NaCl stress shows a great decline in the
osmotic potential as compared with total water potential leading to turgor maintenance
(Rajasekaran et al., 2001).
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1.2.3. Effects of salinity on leaf anatomy and chloroplast ultrastructure
Epidermal thickness, mesophyll thickness, palisade cell length and diameter, and
spongy cell diameter in leaves of bean, cotton, and Atriplex increases with the increase in
salinity (Longstreth and Nobel, 1979). Also, salinity shrinks intracellular spaces in leaves
(Delphine et al., 1998). Salt stress causes (1) development of vacuole and partial swelling
of endoplasmic reticulum, (2) diminishing of mitochondrial cristase and swelling of
mitochondria, (3) vesiculation and fragmentation of tonoplast, and (4) cytoplasm
degradation by cytoplasmic and vacuolar matrices in leaves of potato (Mitsuya et al.,
2000). Additionally, salt stress causes rounding of cells, smaller intercellular spaces, and
a reduction in chloroplast in the leaves of potato (Bruns and Hecht-Buchhloz, 1990).
Salinity reduces leaf area and stomatal density in tomato (Romeroaranda et al., 2001).
In the plants treated with NaCl, electron microscopy reveals the disorganization of
thylakoidal structure of the chloroplasts, increases in the size and number of plastoglobuli,
and decreases in their starch content (Hernandez et al., 1995, 1999). Thylakoid
membranes of chloroplast are swollen and most of them are lost under high salt stress in
the mesophyll cells of sweet potato leaves (Mitsuya et al., 2000). Salinity reduces the
number and depth of the grana stacks, causes swelling of the thylakoid, and starch grains
becomes larger in the chloroplast in potato (Burns and Hecht-Buchholz, 1990).
Transmission electron microscopic analysis shows that the chloroplasts are aggregated,
the cell membranes are distorted and wrinkled, and there are no signs of swelling of grana
or thylakoid structures in the chloroplast of NaCl treated tomato leaves (Khavarinejad
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and Mostofi, 1998). Also, a notable disorganization of the thylakoid structure of
chloroplasts are reported in leaves of B. paraviflora (Parida et al., 2003).
1.2.4. Effects of salinity on photosynthesis, and photosynthetic pigments and
proteins
The photosynthetic rate decreases in salt-treated plants due to several factors: (1)
dehydration of cell membranes that reduce permeability to CO2, (2) salt toxicity to
numerous photosynthetic enzymes, (3) CO2 assimilation reduction due to hydroactive
stomatal closure, (4) enhanced senescence induction, (5) changes in the activity of
enzymes which is induced by changes in their cytoplasmic structure, and (6) negative
feedback due to the reduction in sink activity (Iyengar and Reddy, 1996).
Plant growth as biomass production measures net photosynthesis. Most
environmental stresses that inhibits growth also affect photosynthesis. Salinity
dramatically decreases the rate of photosynthesis and arrests plant growth (Kawasaki et
al., 2001). Plants under high salinity shows reduction in carbon assimilation because of
the accumulation of salt in developing leaves (Munns and Termatt, 1986). High salt stress
inhibits PSII activity (Bongi and Loreto, 1989; Mishra et al., 1991; Masojidek and Hall,
1992; Belkhodja et al., 1994; Everard et al., 1994), whereas some other studies suggested
that it has no such negative effect on PSII (Robindon et al., 1983; Brugnoli and
Bjorkman, 1992; Morales et al., 1992). Several studies indicated that the rate of
photosynthesis may not always be slowed down by salinity and is even stimulated by low
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salt concentration in some species (Rajesh et al., 1998; Kurban et al., 1999). Also, there
are several reports on supression of photosynthesis during salinity stress (Chaudhari and
Choudhuri, 1997; Soussi et al., 1998; AliDinar et al., 1999; Romeroaranda et al., 2001;
Kao et al., 2001). Reduction in leaf area reduces the assimilation of CO2 (Papp et al.,
1983; Munns et al., 2000), mesophyll conductance (Delfine et al., 1998), stomatal
conductance (Brugnoli and Lauteri, 1991; Ouerghi et al., 2000; Agastian et al., 2000;
Parida et al., 2003), and the efficiency of photosynthetic enzymes (Seemann and
Critchley, 1985; Yeo et al., 1985; Seemann and Sharkey, 1986; Brugnoli and Bjorkman,
1992; Reddy et al., 1992).
Salinity decreases the chlorophyll and total carotenoid contents of the leaves. In
leaves of alfalfa grown under high salinity, chlorophyll content and net photosynthetic
rate increases the respiration rate and CO2 compensation concentration, while there are
no notable changes in the carotenoid contents (Khavarinejad and Chapararzedeh, 1998).
Under the prolonged period of salt stress the older leaves start to develop chlorosis and
fall (Hernandez et al., 1995; Gadallah, 1999; Agastian et al., 2000). However, it is
reported that in Amaranthus, chlorophyll content increases under the conditions of
salinity (Wang and Nil, 2000). Salinity stress decreases the total chlorophyll content of
plant leaf by increasing the activity of chlorophyllase, which is a chlorophyll degrading
enzyme (Rao and Rao, 1981), inducing chloroplast destruction and pigment protein
complex instability (Singh and Dubey, 1995).
Salinity decreases the net CO2 assimilation rate and the ratio of ribulose -1, 5-
bisphosphate carboxylase oxygenase (Rubisco) activity to that of phosphoenol pyruvate
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carboxylase (PEPC) in A. lentiformis because PEPC activity on a leaf area basis increases
linearly with salinity, whereas Rubisco activity remains relatively constant (Zhu and
Meinzer, 1999). Furthermore, salinity decreases the soluble protein content in leaves
(Alamgir and Ali, 1999; Gadallah, 1999; Wang and Nil, 2000; Parida et al., 2002). In
mulberry, the soluble protein increases at low salinity and decreases at high salinity
(Agastian et al., 2000).
1.2.5. Effects of salinity on lipids
Lipids acts as insulators of delicate internal organs, which are the most effective
sources of storage energy, and they play vital roles as the structural constituents of most
of the cellular membranes (Singh et al., 2002). Lipids have important roles in the
tolerance of various physiological stressors in a variety of organisms including
cyanobacteria. Phospholipid bilayers are responsible for the dessication tolerance, which
are stabilized during water stress or salt stress by sugars. In peanut the lipid content
increases at low concentration of NaCl (up to 45 mM) and decreases as its concentration
increases (Hassanein, 1999). Plasma membrane vesicles isolated from calli of tomato
tolerant to 100 mM NaCl shows evidence of higher phospholipid and sterol content and
lower phospholipid/free sterol ratio and lower saturated phospholipid fatty acids (Kerkeb
et al., 2001).
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1.2.6. Effects of salinity on ion levels
High NaCl uptake competes with the uptake of other nutrient ions, mostly K+,
leading to K+
deficiency. In a number of plants, increased NaCl increases Na+ and Cl
- and
decreases Ca2+
, K+, and Mg
2+ levels (Khan et al., 1999, 2000; Khan, 2001). In Vicia faba,
salinity enhances the content of Na+, Ca
2+, and Cl
- and decreases the ratio of K
+/Na
+
(Gadallah, 1999). A report indicates a significant increase in Na+ and Cl
- content in
leaves, stem, and root of the mangrove B. parviflora without any considerable alteration
in the endogenous K+ and Fe
2+ level in leaves. Whereas there is decrease in Ca
2+ and
Mg2+
level in leaves upon salt accumulation, suggesting that there is an increase in
membrane stability and decline in chlorophyll content (Parida et al., 2004a).
1.2.7. Effects of salinity on antioxidative enzymes and antioxidants
High salinity causes water deficit as a result of osmotic effects on a wide variety
of metabolic activities in plants. This water deficit in turn results oxidative stress due to
the formation of reactive oxygen species such as superoxides and hydroxy and peroxy
radicals. These reactive oxygen species, which are the by-products of hyper-osmotic and
ionic stresses cause membrane disfunction and cell death (Bohnert and Jensen, 1996).
Plants can induce the activities of certain antioxidative enzymes such as catalase,
peroxidase, glutathione reductase, and superoxide dismutase to scavenge such reactive
oxygen species. In cotton, NaCl stress increases the activities of superoxide dismutase,
guaicol peroxidase, and glutathione reductase and decreases the activities of catalase and
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ascorbate peroxidase (Gossett et al., 1994). Also, there is decrease in total ascorbate, total
glutathione, and α-tocopherol amounts. High salinity enhances the level of H2O2 and the
activities of superoxide dismutase, ascorbate peroxidase, and guaicol peroxidase,
although it decreases catalase activity in leaves of rice (Lee et al., 2001). In leaves of B.
parviflora, salt stress causes increase in ascorbate peroxidase, glutothine peroxidase,
glutothione reductase, and superoxide dismutase activity and decrease in catalase activity
(Parida et al., 2004b).
1.2.8. Effects of salinity on nitrogen metabolism
In nitrogen assimilation, the reduction of NO3-
to NO2-
is catalyzed by nitrate
reductase (NR), which is considered to be the rate-limiting step (Srivastava, 1990; Lea,
1997). In higher plants, protein phosphorylation and dephosphorylation can rapidly shift
the enzymes activity. In the dark, in presence of free Mg2+
, 14-3-3 proteins interact with
phosphorylated NR, resulting in a complete inactivation of NR (Kaiser et al., 1999).
Through this process, NR in leaves is rapidly inactivated in the dark and activated in the
light. It is assumed that salt stress may negatively affect both NR expression and
activation, which ultimately influence NR stability (Huber & Kaiser 1996). In many
plants, salt stress reduces the NR activity (AbdElBaki et al., 2000; Flores et al., 2000). In
addition to the direct effect of Cl- on the enzyme activity, its presence in the external
medium reduces NO3- uptake, which consequently lowers NO3
- concentration in the
leaves (Cram, 1973; Deane-Drummond and Glauss, 1982; Flores et al., 2000). Thus, the
decrease in NR activity and nitrate level in plant under salt stress may reduce the growth
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and biomass production. Nicotinamide adenine dinucleotide phosphate isocitrate
dehydrogenase (NADP-ICDH) is a key cytosolic enzyme that links carbon and nitrogen
metabolism by supplying carbon skeletons for primary nitrogen assimilation in plants.
The activity of NADP-ICDH increases in leaves and decreases in roots of plants adopted
to high salinity, whereas the activity of ferredoxin-dependent glutamate synthase, which
is a key enzyme of nitrogen assimilation and biosynthesis of amino acids, decreases in
leaves in response to the high salinity (Popova et al., 2002). The nitrate and nitrate
reductase content of leaves decreases, but nitrate increases in roots of Zea mays under
high salinity condition (AbdElBaki et al., 2000). Soussi et al., 1999 reported that salinity
inhibits nitrogen fixation by reducing nodulation and nitrogenase activity in chick-pea.
1.2.9. Effects of salinity on malate metabolism
In the chloroplasts of higher plants, NADP-malate dehydrogenase (NADP-MDH)
reduces oxaloacetate to malate. Under salt stress, NADP-MDH decrease transiently in
leaves and then increase to levels greater than two fold higher than levels in unstressed
plants, while transcription levels in roots are extremely low and remain unaffected in the
chloroplasts of M. crystallinum. This salt-stress induced expression pattern of NADP-
MDH suggests its potential role in the CO2 fixation pathway during crassulacean acid
metabolism (CAM) (Cushman, 1993). In NaCl treated Eucalyptus citridora plants, the
malate content decreases in leaves, but the specific activities of NAD and NADP-malic
enzymes increases (DeAragao et al., 1997).
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1.3. Mechanisms of plant salt stress tolerance
Plants battle a saline environment in two principal ways: either by excluding Na+
at the plasma membrane or by sequestering them in the large intracellular vacuole. In
both circumstances accumulation of compatible solutes restores the correct osmolarity to
the intracellular milieu. The Na+/H
+ antiport flow sodium ions in the large vacuole
membrane down an electrochemical proton gradient generated by two vacuolar proton
pumps and accumulate Na+ inside the large intracellular vacuole (Apse et al., 1999).
The toxic levels of sodium ion and the low osmotic potential of soil solution are
responsible for creating the unfavourable multiple effects on plant metabolism, growth
and development at molecular, biochemical and physiological levels (Munns, 2002;
Winicov, 1998; Tester and Devenport, 2003). Proper ion flux regulation is necessary for
cells to keep low toxic ionic concentration and to accumulate essential ions. Intracellular
K+
and Na+ homeostatis is essential for the activities of many cytosolic enzymes,
maintaining mambrane potential, and for the synthesis of osmoticum. Plant cell employ
H+-ATPase mediated primary active transport and channels, and co-transporters mediated
secondary transport. Under salt stress, Na+ enters to plant cells through several pathways
and Na+ stress disrupts K
+ uptake by root cells. These processes results in a decrease in
K+/Na
+ ratio in cytosol. When Na
+ accumulates to the higher level in cytosol, it becomes
toxic to the enzymes. Thus, the abilily of plants to keep low Na+
concentration in cytosol
is the decisive factor for salt tolerance (Yeo, 1998; Maathuis and Amtmann, 1999).
Excess Na+
in cytosol could be removed by the active mechanisms to apoplastic space via
plasma membrane or to vacuole via tonoplast membrane (Aspe et al., 1999; Shi et al.,
Texas Tech University, Manoj Banjara, August 2010
14
2002; Zhang and Blumwald, 2001). Also, there are several other mechanisms which
bolster plants to grow under soil salinity.
1.3.1. Sodium compartmentalization into vacuoles
The largest compartment of a mature plant cell is the central vacuole that occupy
about 80% of the total cell volume. Vacuolar Na+/H
+ antiportors are ubiquitous
membrane proteins that catalyze the exchange of Na+
for H+ across the membrane, which
resolves excessive Na+ in cytosol under saline conditions (Blumwald and Poole, 1985).
Na+/H
+ antiporters are involved in diverse physiological processes, such as salt tolerance,
pH regulation, cell volume, morphogenesis, and extruding the H+ generated during
metabolism (Waditee et al., 2006). These Na+/H
+ antiporters transfer Na
+ into vacuoles,
which are energized by the vacuolar PEG (Proton Electrochemical Gradient) generated
by the vacuolar ATPase (H+-adenosine triphosphatase) and PPase (H
+-pyrophosphatase)
(Blumward, 1987, Gaxiola et al., 2002, Horie and Schroeder, 2004). The consequence of
sequestering cytosolic Na+ into the vacuoles of plant cells is to maintain a low level of
Na+ in cytosol, which minimizes the Na
+ toxicity and injury to important enzymes in
cytosol. In the meantime, the high Na+ concentration in vacuoles would draw more water
into cell and maintain cell turgor (Glenn et al., 1999).
Under salt stress condition, AtNHX1-overexpressing Arabidopsis showed higher
vacuolar Na+/H
+ exchange activity and a salt-tolerant phenotype compared to wild-type
and sequestered more Na+ in plants (Apse et al., 1999), which provided convincing
Texas Tech University, Manoj Banjara, August 2010
15
evidence that Na+/H
+ antiporters in vacuoles play an important role in salt tolerance. In
addition to Arabidopsis gene AtNHX1, overexpression of its homologous genes GhNHX1
from cotton (Gossypium hirsutum), OsNHX1 from rice (Oryza sativa), and CgNHX1 from
Chenopodium glaucum in tobacco and rice also can lead to increase salt tolerance
(Fukuda et al., 2004; Wu et al., 2004; Li et al., 2009). These studies indicate that
overexpression of vacuolar Na+/H
+ antiporters can confer increased salt tolerance in
plants.
1.3.2. Sodium extrusion via the plasma membrane
Another strategy for plants to survive during salt stress is to eradicate cytosolic
Na+ out of the plant cells. Na
+ efflux across the plasma membrane is mediated by Na
+/H
+
antiportors (DuPont, 1992). In the plasma membrane of barley roots, K+-prompted Na
+
efflux was observed (Rather and Jacoby, 1976). The observation of change in pH
gradient across the plasma membrane in wheat and barley indicate the possibility of
having Na+/H
+ antiporter to transport Na
+ out of cytoplasm (Mennen et al., 1990).
Additionally, antiporter activity was observed in plasma membrane vesicles of wheat
(Allen et al., 1995), tomato (Wilson and Shannon, 1995), and cotton (Hassidim et al.,
1990). Na+/H
+ transporters and other cation/proton transporters at the plasma membrane
efflux Na+ and other cations out of the cell due to the establishment of proton motive
force across the plasma membrane by plasma membrane type ATPase (Schachtman and
Liu, 1999). The sequestration of Na+ out of the cell in apoplast through the Na
+/H
+
antiporter at the plasma membrane is an effective approach to maintain intracellular ion
Texas Tech University, Manoj Banjara, August 2010
16
homeostasis (Bartels and Nelson, 1994; Zhu, 2001). However, the energy expense is the
critical factor for the Na+ dismisal for salinity responses (Davenport and Tester, 2000).
The secondary active Na+/H
+ antiporters SOS (Salt Overly Sensitive) were
identified as crucial components in Na+ exclusion through the plasma membrane, which
are responsible for salt tolerance in Arabidopsis (Zhu, 2003). Jain-Kang Zhu and his co-
workers identified three components of a stress-signaling pathway SOS1, SOS2, and
SOS3, which controls ion homeostasis and salt tolerance (Hasegawa et al., 2000; Sanders,
2000; Zhu, 2000; 2001). SOS1 (AtNHX7) gene encodes a Na+/H
+ antiporter that has 12
hydrophobic transmembrane domains in the N-terminal and a long hydrophilic C-
terminal tail, and the SOS1-GFP (green fluorescence protein) fusion data suggests that
the SOS1 Na+/H
+ antiporter is localized on the plasma membrane (Shi et al., 2000). SOS3
(AtCBL4) gene encodes a Ca2+
binding protein capable of sensing the cytosolic Ca2+
signal elicited by salt stress (Liu and Zhu, 1998; Ishitani et al., 2000). If the Ca2+
-binding
capacity of SOS3 is reduced due to mutation, the mutant becomes hypersensitive to salt,
indicate its importance in salt stress signaling (Zhu, 2002). SOS2 (AtCIPK24) gene
encodes a serine/threonine protein kinase known as the CBL-interacting protein kinase
(CIPK) that interacts physically with SOS3 (Liu et al., 2000; Halfter et al., 2000). In a
calcium dependent manner, SOS3 activates the protein kinase activity of SOS2 (Mahajan
et al., 2006). Lower rate of Na+-stimulated proton transport occurred in plasma
membrane vesicles from sos1, sos2, and sos3 mutant plants in comparision to those of the
wild-type plants (Qiu et al., 2002). Several evidence suggests that SOS1 is one of the
target of SOS signal transduction pathway whose activity is controlled by SOS2/SOS3
(Guo et al., 2001; Qiu et al., 2002; Zhang et al., 2004). Therefore, the mechanism to
Texas Tech University, Manoj Banjara, August 2010
17
extrude excess Na+ from the cytosol via plasma membrane enables plants to grow under
high salt condition.
1.3.3. Synthesis or accumulation of osmoprotectants
Under excess Na+ concentration, either Na
+ is compartmentalized into the vacuole
or excluded out of the cell to keep optimum cytosolic Na+, the osmotic potential in the
cytoplasm must be stabilized with that in the vacuole and extracellular environments to
guarantee the maintenance of cell turgor and uptake of water for cell growth. This
requires an increase in osmolytes in the cytosol, either by uptake of soil solutes or by
synthesis of metabolically compatible solutes. These compatible solutes include largely
proline (Khatkar and Kuhad, 2000; Singh et al., 2000), glycine betaine (GB) (Rhodes and
Hanson, 1993; Khan et al., 2000; Wang and Nil, 2000), sugars (Kerepesi and Galiba,
2000; Bohnert and Jensen, 1996; Pilon-Smits et al., 1995), and polyols (Ford, 1984; Popp
et al., 1985; Orthen et al., 1994; Bohnert et al., 1995) that do not inhibit cellular
biochemical reactions. These solutes can also act as free-radical scavengers or chemical
chaperones, which directly stabilize membranes and/or proteins (Akashi et al., 2001;
Hare et al., 1998; Bohnert and Shen, 1999; McNeil et al., 1999; Diamant et al., 2001).
One of the osmoprotectants, polyols, functions in two ways: osmotic adjustment
and osmoprotection. In osmotic adjustment, they facilitate the retention of water in the
cytoplasm and allow Na+ sequestration to the vacuole or apoplast. These osmolytes have
H-bonding characteristics that allow them to interact with membranes, protein
Texas Tech University, Manoj Banjara, August 2010
18
complexes, or enzymes to protect macromolecules from the adverse effects of increasing
ionic strength in the surrounding media (Crowe et al., 1992). Under the salt stress,
carbohydrates such as sugars (glucose, fructose, sucrose, fructans) and starch accumulate
in the plant (Parida et al., 2002) and function on osmoprotection, osmotic adjustment,
carbon storage, and radical scavenging. It is demonstrated that the increase in compatible
solutes such as glycine betaine, sorbitol, mannitol, trehalose, and proline in engineered
plants improved the tolerance to drought stress, high salinity and cold stress (Chen and
Murata, 2002; He et al., 2007). Therefore, compatible solute biosynthesis is an important
mechanism to enable plants to survive under salinity.
1.3.4. Induction of antioxidative enzymes
Salt stress impose water deficit, which leads to the formation of reactive oxygen
species (ROS) like superoxide, hydrogen peroxide, hydroxyl radical and singlet oxygen
(Halliwell and Gutteridge, 1985; Elstner, 1987). These cytotoxic oxygen species can
seriously disturb the normal metabolism through the oxidative damage to lipids, proteins,
pigments, and nucleic acids (Fridovich, 1986; Wise and Naylor, 1987; Imlay and Linn,
1988). Chloroplast is prone to generate activated oxygen species, since there is high
internal oxygen in chloropast during photosynthesis (Asada and Takahashi, 1987).
Certain antioxidative enzymes such as catalase (CAT), ascorbate peroxidase (APX),
glaicol peroxidase (POD), glutathione reductase (GR), and superoxide dismutase (SOD)
scavenge such reactive oxygen species. The activities of the antioxidative enzymes such
as CAT, APX, POD, GR, and SOD increase under salt stress in plants whose actions
Texas Tech University, Manoj Banjara, August 2010
19
allow plants to survive under salt stress (Gossett et al., 1994; Hernandez et al., 1995,
2000; Sehmer et al., 1995; Kennedy and De Fillippis, 1999; Sreenivasulu et al., 2000;
Benavides et al., 2000; Lee et al., 2001; Mittova et al., 2002, 2003). The activities of
APX, CAT, and GR decrease, while SOD and reduced glutathione increase, and
malondialdehyde and total proteins remain constant in the root nodule of soybean under
high salinity (Comba et al., 1998). In B. gymnorrhiza, salt stress leads to the generation of
superoxide, which is scavenged by the oxygen-scavenging system of the cytosol and
contributes to the salt tolerance capacity (Takemura et al., 2002).
1.3.5. Induction of plant hormones
High salt concentration stimulates the synthesis of plant hormones like abscisic
acid (ABA) and cytokinins (Thomas et al., 1992; Aldesuquy, 1998; Vaidyanathan et al.,
1999). ABA regulates ion fluxes in guard cells and promotes stomatal closure under salt
stress condition. Also, ABA alters the expression of salt-stress-induced genes (de
Bruxelles et al., 1996), which are predicted to play an important role in the mechanism of
salt stress tolerance in rice (Gupta et al., 1998). Inhibitory effects of NaCl on
photosynthesis, growth, and translocation of assimilates were alleviated by ABA (Popova
et al., 1995).
Texas Tech University, Manoj Banjara, August 2010
20
1.3.6. Change in photosynthetic pathway
Reduction of water potential in salt stress inhibits photosynthesis. Thus, the main
aim of salt tolerance is to increase water use efficiency under salinity. Atriplex lentiformis
shift from the C3 to the C4 photosynthetic pathway to maximize photosynthesis under
salinity (Zhu and Meinzer, 1999). M. crystallinum shift to CAM from C3 photosynthetic
pathway and decrease transpiratory water loss under prolonged salinity condition
(Cushman et al., 1989).
1.4. Characteristics of sodium/proton antiporter
Na+/H
+ exchangers are ubiquitious membrane proteins, which catalyze the
exchange of Na+ for H
+ across membranes. These antiporters play important roles in salt
tolerance, cell volume, pH regulation, morphogenesis, and extruding the H+ generated
during the time of metabolism (Waditee et al., 2006). Arabidopsis genome sequencing
suggests the presence of more than 38 Na+/H
+ exchanger homologs, among which
vocuolar AtNHX1 and the plasma membrane SOS1 are two extensively studied
antiporters (Figure 1.1.).
The analysis of genes involved in cation detoxification in yeast led to the
identification of a Na+/H
+ antiport (NHX1). NHX1 was localized to a prevacuolar
compartment and showed a high degree of amino acid sequence similarity to Na+/H
+
antiports from Caenorhabditis elegans and human (NHE6, mitochondrial). The
Arabidopsis thaliana genome-sequencing allowed for the identification of a plant gene
Texas Tech University, Manoj Banjara, August 2010
21
AtNHX1, which is similar to bacterial, fungal, and mammalian homologous (Apse et al.,
1999; Frommer et al., 1999; Waditee et al., 2006).
The overexpression of vacuolar Na+/H
+ antiporters could serve as a good model
for the engineering of salt tolerant crops (Apse et al., 1999). The overexpression of a
single endogenous Arabidopsis thaliana gene AtNHX1 that encodes a vacuolar
membrane-bound Na+/H
+ antiport should possibly engineer a large spectrum of salt
tolerant crop plants, enabling them to tolerate relatively high salt conditions. Continuous
overexpression of AtNHX1 in transgenic Arabidopsis results in the salt-resistant
phenotype (Apse et al., 1999; Frommer et al., 1999).
Proton electrochemical gradient (PEG) establishment across the tonoplast drives
Na+ import from the cytosol to the vacuole via the Na
+/H
+ antiporter, which determines
the capicity of salt tolerance in plants (Blumwald, 2000). This antiporter protein consists
of 538 amino acids, which has several transmembrane domains, and an amiloride-binding
site (Gaxiola et al., 1999; Hamada et al., 2001). Topological analysis of AtNHX1
demonstrates that there are 9 transmembrane domains, 3 membrane-associated
hydrophobic domains, an N-terminus facing towards cytosol, and a hydrophilic C-
terminus dwelling in the vacuolar lumen, which regulates the exchange of Na+/H
+. C-
terminus deletion of AtNHX1 enhanced Na+/H
+, but lower K
+/H
+ exchange rate
(Yamaguchi et al., 2003).
Vacuolar Na+/H
+ antiporters encoded by NHX gene catalyze the exchange of Na
+
for H+
across the vacuolar membranes and compartmentalize Na+ into vacuoles (Nass et
al., 1997; Blumwald, 2000; Hasegawa et al., 2000). In plants, the sequestration of toxic
Texas Tech University, Manoj Banjara, August 2010
22
sodium ions into vacuoles through Na+/H
+ antiporters mainly results in salt tolerance
(Apse and Blumwald, 2002; Zhu, 2003; Tester and Davenport, 2003).
It is demonstrated that the expression of introduced NHX genes in transgenic
plants are responsive to NaCl treatment in most cases, and overexpression of the NHX
genes in the transgenic Arabidopsis, tomato, wheat, cabbage, rapeseed, cotton, rice,
tobacco, tall fescue, and Petunia hybrida expressed higher levels of NHX protein and
displayed an increased vacuolar uptake of Na+ than wild-type plants, which is responsible
for increased salt tolerance (Apse et al., 1999; Fukuda, 1999; Zhang and Blumwald,
2001; Zhang et al., 2001; He et al., 2005; Fukuda et. al., 2004; Duan et al., 2009; Tian et
al., 2006; Xu et al., 2009; Ohta et al., 2002; Wu et al., 2004; Xue et al., 2004).
1.5. Strategy to make salt tolerant plants
The major limiting factors in agricultural productivity are salinity and drought
(Boyer, 1982; Bartels and Sunkar, 2005), which are becoming more serious with global
warming (Gale, 2002; Grover et al., 2003). Even though better farm management
practices such as better irrigation, phase farming, intercropping and precision farming
could somewhat mitigate the salinity in soil (Munns, 2002), it takes huge amount of
money and very long time to improve soil quality suitable for crop growth. Thus, it is
essential for researchers to develop breeding strategies and advance technologies to make
crops more productive under high salinity conditions (Cushman and Bohnert, 2000).
Texas Tech University, Manoj Banjara, August 2010
23
Plant breeders were unsuccessful in generating salt tolerant varieties utilizing
genetic variation arising from restricted varietal germplasm and interspecific
hybridization to induce mutations and somaclonal variation of cell and tissue cultures
(Flowers and Yeo, 1995). Lacks of efficient selection techniques, complexity of salt
tolerance mechanisms and narrow genetic background have limited the development of
efficient conventional approach for the improvement of salt tolerant crops (Cushman and
Bohnert, 2000). However, the progress in the study of biochemical mechanisms of plant
stress responses and salt tolerance, molecular cloning of genes encoding major
components in the signal transduction and metabolic pathway that respond to salt stress,
and the development of genetic transformation technology for many crop species have
made it possible to generate salt-tolerant crops (Bohnert and Jensen, 1996; Winicov and
Bastola, 1997).
In opposition to traditional breeding, genetic engineering technique seems to be a
more efficient and rapid approach to introduce a small number of genes to improve salt
tolerance. Present engineering approaches rely on the transfer of one or several genes,
which are important in biochemical pathways or endpoints of signaling pathways. The
transgenic technology has great potential to generate plants that are capable of growing in
soil of high salinity and improving agricultural productivity by manipulating the
biosynthesis of compatible solutes to enhance ion homeostasis, increasing antioxidation
to diminish oxidative damage, overexpressing Na+/H
+ antiporter genes to reduce the Na
+
level in the cytoplasm (Apse et al., 1999; Zhang and Blumwald, 2001; Zhang et al.,
2001; Shi et al., 2003; Fukuda et al., 2004; Wu et al., 2004; Xue et al., 2004; Ashraf and
Harris, 2004).
Texas Tech University, Manoj Banjara, August 2010
24
1.6. Basis for creating transgenic peanut with higher salt stress tolerance
It is necessary to understand plants response to salinity and water deficit
conditions at the cellular and molecular level for the generation of transgenic crops with
improved stress tolerance (Wang et al., 2003; Zhang et al., 2004). Salinity tolerance is a
complex multigenic trait in which large number of genes are responsible for encoding
salt-stress proteins such as (1) genes that synthesize compatible solutes, (2) genes for
photosynthetic enzymes (3) genes that encode proteins to sequester Na+
into the vacuole
or efflux Na+ to the apoplast, and (4) genes for radical-scavenging enzymes (Parida and
Das, 2005). Glycophytic plants have sodium compartmentalization and exclusion
mechanisms to maintain low cytosolic sodium concentration.
A well known mechanism to transport sodium out of the cell is through the
operation of a secondary active Na+/H
+ antiporters, SOS1, which are responsible for salt
tolerance in Arabidopsis (Zhu, 2003; Shi et al., 2002). Furthermore, the efficient
compartmentalization of sodium is accomplished through the operation of vacuolar
Na+/H
+ antiporters that remove potentially harmful Na
+ from the cytosol into the large
tonoplast-bound vacuoles (Apse et al., 1999). Accumulation of ions in the vacuole acts as
an osmoticum to maintain water flow into the cell (Glenn et al., 1999; Gaxiola et al.,
2002).
Texas ranks second among the peanut producing states of US whose 70%
production relies on West Texas region. The productivity of this very important crop in
West Texas is negatively affected by low water and high salinity. Genetic engineering
techniques can be employed to generate transgenic peanuts to alleviate the loss of peanut
Texas Tech University, Manoj Banjara, August 2010
25
yield due to the harsh environmental factors. Therefore, the main goal of this study was
to introduce an Arabidopsis gene AtNHX1 into peanut for the generation of transgenic
peanut which would be more tolerant to high salinity because of its enhanced capability
to compartmentalize Na+ into vacuoles (Figure 1.1.). Accordingly, as a part of this project
I have achieved the following two aims: (1) Creation of AtNHX1-expressing peanut
plants, and (2) physiological and biochemical analysis of AtNHX1-expressing peanut
plants for salt tolerance in greenhouse.
Texas Tech University, Manoj Banjara, August 2010
26
Figure 1.1. Model for Na+ regulation in plant cell. A. Transporters regulating Na
+ levels
in a normal plant cell. B. Transporters regulating Na+ levels in an AtNHX1-expressing
plant cell.
A
B
Texas Tech University, Manoj Banjara, August 2010
27
CHAPTER II
MATERIALS AND METHODS
2.1. Vector construction and peanut transformation
The amplified full-length coding sequence of AtNHX1 from Arabidopsis cDNA
library was subcloned into the dephosphorylated Bam HI site of the intermediate vector
pRTL-2 (gift from James Carrington, Oregan State University) under the control of the
CaMV 35S promoter. Afterward, Hind III was used to digest the construct and the
fragment was ligated into the Hind III site of the binary vector pCGN-1578 that has the
neomycin phosphotransferase gene, Npt II, as the selective marker (McBride and
Summerfelt, 1990) (He, 2005). The overexpression construct (Fig. 2.1) was then
introduced into the Agrobacterium tumefaciens stain GV3101. These GV3101 harboring
pCGN-1578 were used to transform peanut plants following the methods described by
Sharma and Anjaiah (2000) with some modifications.
For co-cultivation, GV3101 Argobacterium stain with plasmid comprising
AtNHX1 was inoculated into 10 ml Luria-Bertani (LB) medium with antibiotics
kanamycin (50 µg/ml), rifampicin (50 µg/ml), and gentamycin (25 µg/ml), and grown
overnight at 30 ºC under constant shaking at 250 rpm, then centrifuged to separate
medium and diluted with MS (Murashige and Skoog) basal salt (2.15 mg/ml).
Runner-type (Flavor runner 458 variety) peanut seeds were surface sterilized by
soaking in 70% ethanol for 1 min, followed by rinsing with 0.1% (w/v) aqueous mercuric
Texas Tech University, Manoj Banjara, August 2010
28
chloride for 10 min, then the seeds were washed at least three times with sterile distilled
water, and soaked in sterile water for about 3 hr prior to use. After taking the seed coat
away from the soaked peanut seeds, the embryo axis was surgically removed and each
cotyledon was cut into vertical halves to obtain the cotyledon explants. The cotyledon
explants were submerged in the Agrobacterium solution for 1 min, blotted on sterile
paper towels, and were placed on the shoot induction medium (SIM) such that the cut
edges were embedded into the medium. The explants plated on plates with SIM medium
that was comprised of MS basal salt (4.3 mg/ml), N6-benzyladenine (6-BA) (5 µg/ml), 2,
4-dichlorophenoxyacetic acid (2, 4-D) (1 µg/ml), glucose (30 mg/ml), and agar (0.8
mg/ml) at pH 5.8 were incubated at 26 ºC for 3 days of co-cultivation in the dark. They
were then transferred to SIM plates containing MS basal salt (4.3 mg/ml), 6-BA (5
µg/ml), 2, 4-D (1 µg/ml), glucose (30 mg/ml), cefotaxime (250 µg/ml), and agar (0.8
mg/ml) at pH 5.8 and incubated at 26 ºC, 100 μmol m-2
s-1
for 15 days. The explants with
induced adventitious shoot buds were excised and transferred to selective SIM bottles
containing MS basal salt (4.3 mg/ml), 6-BA (5 µg/ml), 2, 4-D (1 µg/ml), glucose (30
mg/ml), kanamycin (100 µg/ml), cefotaxime (250 µg/ml), and agar (0.8 mg/ml) at pH 5.8
for 15 days. Then the explants bearing shoot buds were transferred to the shoot
elongation medium (SEM) having MS basal salt (4.3 mg/ml), 6-BA (0.5 µg/ml), 2, 4-D
(1 µg/ml), glucose (30 mg/ml), kanamycin (100 µg/ml), cefotaxime (250 µg/ml), and
agar (0.8 mg/ml) at pH 5.8 and subcultured every 15 days twice or three times for the
development of adventitious shoot buds. The elongated shoots were transferred to the
root induction medium (RIM) comprising MS basal salt (4.3 mg/ml), glucose (30 mg/ml),
α-naphthaleneacetic acid (NAA) (1 µg/ml), and phytagel (0.2 mg/ml) at pH 5.8 and
Texas Tech University, Manoj Banjara, August 2010
29
incubated at 26 ºC, 100 μmol m-2
s-1
until a good root system develop. The young
transgenic plants with good root system were then transplanted into soil in plastic pots.
Transgenic plants were allowed to adapt at low moisture in the growth chamber for few
weeks before transplanting them into big pots in greenhouse at 28 ± 2 ºC or in field. DNA
and RNA were extracted from the leaves of T0 plant (transgenic plant generated from
tissue culture) to identify true transgenic lines. Seeds harvested from T0 plants, T1 were
used for the subsequent experiments in greenhouse.
2.2. Isolation of genomic DNA and PCR analysis of putative transformants
The PowerplantTM
DNA isolation kit (MO BIO Laboratories, Inc., CA, USA) was
used to isolate genomic DNA from fresh leaves of greenhouse and field-growing peanut
plants. Concentration and purity of genomic DNA was determined by NanoDrop® (ND-
1000 spectrophotometer, NanoDrop Technologies, Wilmington, Delaware, USA).
Polymerase chain reaction (PCR) was carried out with thermacycler
(Mastercycler Gradient, Eppendorf, Hamburg, Germany) to amplify the AtNHX1 gene
using the EcnoTaq® DNA polymerase (Lucigen Corporation, Greenview Drive
Middleton, WI, USA). Primers were designed based on the known sequences of target
AtNHX1 gene. The 25 µl PCR reaction mixture contained 5 µl genomic DNA (~0.1
µg/µl), 2.5 µl 10X EconoTaq reaction buffer containing; 10 mM Tris-HCl (pH 9.0), 500
mM KCl, 15 mM MgCl2, and 1% Triton X-100, 2 µl dNTP (2.5 mM concentration for
each of the four different deoxyribonucleotides), 1µl forward primer (0.1 µg/µl, 5'-
TGATTGGGCTAGGCACTG -3'), 1µl reverse primer (0.1 µg/µl, 5'-
Texas Tech University, Manoj Banjara, August 2010
30
CAGCTTCGTGGTTTAGGTGA -3'), 0.25 µl thermo tolerant EconoTaq DNA
polymerase enzyme, and 13.25 µl H2O. The amplification reactions were carried out
under the following conditions: an initial denaturation at 94 °C for 4 min, followed by
35 denaturation cycles at 94 °C for 1 min, annealing at 52 °C for 30 sec, and extension at
72 °C for 30 sec, and a final extension at 72 °C for 10 min. The amplified products were
segregated by electrophoresis on 0.8% agarose gels with ethidium bromide (EtBr) and
visualized under UV-light.
2.3. Isolation of total RNAs and RNA blot analysis
All materials (mortar, pestle and buffers) used in this experiment were washed
with diethyl pyrocarbonate (DEPC) treated water. One gram of leaf tissues from each
sample (transgenic and wild-type peanut plants) were ground into fine powder using
mortar and pestle in liquid N2, then homogenized mixing with 1 ml of TRIzol reagent
(Invitrogen Corporation, Van Allen Way Carlsbad, CA, USA) in 1.5 ml microcentrifuge
tube. After incubating the sample at room temperature for 5 min, 200 µl chloroform was
added, followed by shaking and vortexing. The samples were again incubated at room
temperature for 3 min. Later on supernatant was transferred into a new tube, from the
sample centrifuged at 3,800 rpm for 20 min at 4 °C. Equal volume of isopropyl alcohol
was mixed to the sample and placed in -20 °C for 45 min, and then centrifuged for 20
min at 13,100 rpm at 4 °C. The supernatant was discarded and once the pellet was
washed with 1 ml of 75% ethanol, sample was air dried. The pellet was dissolved in 90 µl
of 0.5% sodium dodecyl sulfate (SDS) applying heat for 10 min at 55 °C. The samples
Texas Tech University, Manoj Banjara, August 2010
31
were then centrifuged at 1,200 rpm for 2 min at room temperature and the supernatant
was collected and transferred to a fresh tube and 1/10 sample volume of 3 M sodium
acetate along with 3 times ice-cold 100% alcohol was added. The sample were mixed by
inversion and placed in -80 °C for 2 hr then centrifuged at 13,100 rpm for 20 min at 4 °C.
The pellet was washed in 75% alcohol, air dried, and re-suspended in 0.5% SDS. It was
re-dissolved by heating at 55 °C for 10 min, then centrifuged for 2 min at 1,200 rpm and
supernatant was placed in new sterile microcentrifuge tube. The RNA concentration and
purity was measured using NanoDrop® (ND-1000 spectrophotometer, NanoDrop
Technologies, Wilmington, Delaware, USA). The ratio of A260/A280 ranged from 1.7 to
1.9 indicates the purity of RNA was enough for Northern blot.
Under the denaturing condition in 37% formaldehyde total RNA was resolved by
electrophoresis in a 1.2% agarose gel. Using the 4-morpholinepropanesulfonic acid
(MOPS) buffer system RNA was transferred to Biotrans™ nylon membrane (MP
Biomedicals, Inc., Irvine, California, USA) using capillary transfer method overnight
(Maniatis et al., 1982). RNA was cross-linked to the membrane using Fisher UV cross-
linker at the optimum setting and was air dried for 3 hr in room temperature on a piece of
towel-paper. The membrane was pre-hybridized in the pre-hybridizing buffer [1% bovine
serum albumin (BSA), 1 mM EDTA (pH 8.0), 0.5 mM NaHPO4 (pH 7.2) and 7% SDS]
for an hr at 64 °C. At 62 ºC, overnight hybridization to the denatured 32
P-labeled probe
was done in the hybridizing solution [1% BSA, 1 mM EDTA (pH 8.0), 0.5 mM
NaHPO4 (pH 7.2) and 7% SDS]. The random-priming method using DECA PrimeTM
II
kit (Ambion Inc., Woodward Street, Austin, TX, USA) was employed to make the
Texas Tech University, Manoj Banjara, August 2010
32
labeling probe (Feinberg and Vogelstein, 1983), which was mixed with hybridizing
solution before starting overnight hybridization. The membrane was washed first with
the concentrated washing solution [0.5% BSA, 1 mM EDTA (pH 8.0), 40 mM NaHPO4
(pH 7.2), and 5% SDS] for 5 min at room temperature, and at least two times with a
diluted solution [1 mM EDTA (pH 8.0), 40 mM NaHPO4 (pH 7.2), and 1% SDS] at 64
ºC for 5 min each in a water bath. The membrane was then wrapped by a plastic wrap
and exposed to the phosphor screen (Amersham Biosciences, Piscataway, NJ, USA)
for 5 hr. Radioactivity was detected scanning phosphor screen by the STORM860
scanner system (Amersham Biosciences 2002, Piscataway, NJ, USA). The membrane
was stripped using the stripping solution [2 mM Tris (pH 8.0), 2 mM EDTA (pH 8.0),
and 0.08% SDS] at least for two times at 74 ºC for 10 min each until the radioactivity is
completely lost. Then the membrane was used for next hybridization as described above.
2.4. Salt treatment
AtNHX1-expressing transgenic T1 and wild-type seeds of peanut were germinated
and grown in greenhouse for 21 days prior to salt treatment which was conducted in
increasing manner, starting from 30 mM NaCl for 6 days, followed by 60 mM, 90 mM,
120 mM, and 150 mM for 6 days, respectively. The temperature and humidity was
maintained at 28 ± 2 °C and 50 ± 10% respectively throughout the growth period in
greenhouse. The experiment was repeated two times.
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33
2.5. Plant growth and biomass measurement under salt treatment in greenhouse
Fresh aboveground and underground biomass were determined after 150 mM
NaCl treatment. Roots were analyzed after gentle flushing of soil by water and drying
with paper towel. Subsequently, dry above and underground biomass was weighed after
drying shoots and roots for 15 days under light in greenhouse.
2.6. Gas-exchange measurements
Rate of photosynthesis, stomatal conductance, and rate of transpiration were
measured by using a portable photosynthesis system (Model LI-COR 6400, Li-Cor, Inc.,
Lincoln, NE, USA) at an ambient CO2 concentration of 400 μmol mol-1
, 60% relative
humidity, 28 °C, and a light intensity of 2000 μmol m-2
s-1
. Instrument was stabilized as
per manufacturer’s guidelines. Before taking measurements, steady state levels of
reference CO2 and reference H2O were observed and infra-red gas analyzers (IRGAs)
were matched manually. Mean of five measurements from each sample were taken for
analysis.
The same photosynthetic system was used to measure the response on CO2
assimilation rate (A) to the change in internal CO2 concentration (Ci) for the
characterization of photosynthetic performance of AtNHX1-expressing and wild-type
peanut plants. The ACi curves were conducted at saturated photosynthetic photon flux
density (PPFD) of 2000 μmol m-2
s-1
, where the reference and sample IRGAs were
matched automatically before taking each measurement. The curves were initiated at 0 Pa
Texas Tech University, Manoj Banjara, August 2010
34
CO2 and increased step-wise to 200 Pa CO2 as described in He et al. (2007). Photosyn
Assistant software (ver. 1.1.2; Dundee Scientific, UK) was used to estimate the
photosynthetic parameters such as Vcmax (the maximum rate of carboxylation by Rubisco),
and Jmax (the light-saturated rate of maximum electron transport). Afterward, these
parameters were used to estimate Asat (net photosynthesis at saturating PPFD), and Amax
(photosynthetic capacity at saturating PPFD and saturating atmospheric CO2) based on
the description provided in Van Gestel et al. (2005).
2.7. Total chlorophyll measurement
The relative amount of chlorophyll was measured by using a portable chlorophyll
meter SPAD-502PLUS (Konica Minolta, Japan), which calculates a numerical SPAD
value measuring the absorbance of leaves in the red and near-infrared regions, which is
proportional to the amount of chlorophyll present in leaves. At each evaluation the
content was measured at the center of each leaflets of every primary leaf and the average
was used for analysis.
2.8. Statistical analysis
Microsoft®
Office Excel 2007 was used for all statistical analysis, which was
performed using student’s t-test considering one tailed, two sample unequal variance. The
significance level was used in hypothesis testing. P values were calculated from the
comparison between wild-type plants and transgenic lines. P < 0.05 and P < 0.01 are two
Texas Tech University, Manoj Banjara, August 2010
35
significance levels, which indicates the probability of rejecting a hypothesis set at 5% and
1% respectively.
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Figure 2.1. AtNHX1-expression construct used for peanut transformation. LB and RB are
the left and right border sequences of the Ti plasmid in the pCGN1578 binary vector. The
drawing is not in scale.
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37
CHAPTER III
RESULTS
3.1. Creation of AtNHX1-expressing peanut
It has been demonstrated that vacuolar Na+/H
+ antiporter overexpressing plants
are more salt tolerant (Apse et al., 1999; Fukuda, 1999; Zhang and Blumwald, 2001;
Zhang et al., 2001; He et al., 2005; Fukuda et. al., 2004; Duan et al., 2009; Tian et al.,
2006; Xu et al., 2009; Ohta et al., 2002; Wu et al., 2004; Xue et al., 2004). Therefore, my
goal was to introduce the Arabidopsis thaliana gene AtNHX1 in peanut for the increased
expression of the vacuolar Na+/H
+ antiporter. My hypothesis behind the project was: (1)
Overexpression of AtNHX1 in peanut will enhance vacuolar Na+ sequestration, resulting
in decreased Na+ concentration in cytosol, and ultimately, improved salt stress tolerance;
(2) Increased Na+ concentration in vacuoles will result in decreased cellular water
potential and increase water uptake under salt conditions, increasing water retention in
peanut.
The AtNHX1 gene was introduced into the genome of peanut through the
Agrobacterium-mediated transformation (Sharma and Anjaiah, 2000). Seedlings
generated from the cotyledon explants were transferred to soil and once they were
acclimated in growth chamber, plants were moved to greenhouse or field. Eighty
independent transgenic lines were generated from tissue culture, but only fifteen lines
gave T1 seeds enough for subsequent physiological and biochemical tests due to the
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38
unfavourable greenhouse and field conditions for peanut growth and seed formation in
our facility.
3.2. Molecular analyses of AtNHX1-expressing transgenic peanut plants
To confirm the insertion of AtNHX1 in the genome of putative transgenic peanut
plants, genomic DNA was extracted from the young leaves of 12 independent putative
transgenic lines and analyzed through PCR. PCR analysis data indicated that 11
independent transgenic lines contain the introduced AtNHX1 in their genome (Fig. 3.1).
Subsequently, RNA bolt analysis was performed to identify transgene transcript, which
showed that at least 3 out of 8 transgenic lines highly expressed AtNHX1 at the transcript
level (Fig. 3.2). These three lines together with other putative lines were then chosen for
later physiological analyses.
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39
Figure 3.1. Analysis of putative AtNHX1-expressing peanut plants by PCR. Genomic
DNAs from wild-type plant and 12 putative transgenic lines were amplified by PCR
using AtNHX1-specific primers. WT, wild type peanut of Runner genotype; 4-12, 14 and
15, eleven independent transgenic peanut lines harboring AtNHX1; 13, independent
transgenic peanut line that does not contain AtNHX1.
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Figure 3.2. RNA blot analysis of wild-type and AtNHX1-expressing plants. WT, wild-
type peanut of Runner genotype; 7, 11, 15, three independent transgenic lines expressing-
AtNHX1 transcripts. The 18S rRNA was used as the internal loading control. The genes
used as probes are listed on the right.
AtNHX1
18s rRNA
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41
3.3. AtNHX1-expressing peanut plants are more salt tolerant
To test the salt tolerance of AtNHX1-expressing peanut plants, 8 independent lines
including three high expressing lines of transgenic plants were analyzed in greenhouse
under saline conditions. The 3 week-old seedlings were watered with 30 mM NaCl for 6
days, followed by 60 mM, 90 mM, 120 mM, and 150 mM NaCl each for 6 days,
respectively. When the NaCl concentration reached 150 mM NaCl, the phenotypic
differences were noticeable between wild-type and AtNHX1-expressing peanut plants.
After finishing the salt treatment, the growth of all plants was analyzed. The AtNHX1-
expressing peanut plants were bigger and bushier than the control wild-type plants (Fig.
3.3). Also, there were large numbers of chlorotic leaves in wild-type peanut plants
relative to AtNHX1-expressing transgenic plants. On the other hand, plants grown under
normal conditions had no apparent phenotypic differences between wild-type and
AtNHX1-expressing peanut plants (data not shown).
To quantify the phenotypic differences between wild-type and AtNHX1-
expressing lines, I measured the fresh and dry biomass of aboveground and underground
portion of peanut plants. The fresh shoot biomass of AtNHX1-expressing peanut plants
were 55% to 58% higher than that of wild-type plants (Fig. 3.4A). Similarly, root
biomass of transgenic lines were 59% to 70% more than wild-type, which is even higher
than shoot biomass (Fig. 3.4B). In addition to the fresh biomass, dry biomass analysis
also confirmed better shoot and root biomass in AtNHX1-expressing lines than wild-type
peanut plants (Fig. 3.5A and Fig. 3.5B). Due to the better root development and shoot
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42
growth, better yield of peanut is anticipated with AtNHX1-expressing peanut plants under
salt conditions in the field.
To measure the greenness or relative chlorophyll content of leaves, SPAD values
were examined using the chlorophyll meter. SPAD reading indicates the plant nitrogen
status, which is important for growth, development, protein, and yield of plant. It is
demonstrated that the leaves of NaCl treated AtNHX1-expressing peanut plants has higher
nitrogen content and hence the amount of chlorophyll than wild-type peanut plants (Fig.
3.6), where as there is no such difference among the plants grown under normal
conditions (data not shown).
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Figure 3.3. Phenotypes of wild-type and AtNHX1-expressing peanut plants after 150 mM
NaCl treatment. WT, wild-type peanut of Runner genotype; 7 and 11, two independent
AtNHX1-expressing peanut lines.
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Figure 3.4. Fresh biomass of wild-type and AtNHX1-expressing peanut plants after 150
mM NaCl treatment. A. Fresh shoot weight. B. Fresh root weight. WT, wild-type peanut
of Runner genotype; 7 and 11, two independent AtNHX1-expressing peanut lines. Values
are mean ± SD (n = 4). ** statistically significant at P < 0.01.
A
B
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Figure 3.5. Dry biomass of wild-type and AtNHX1-expressing peanut plants after 150
mM NaCl treatment. A. Dry shoot weight. B. Dry root weight. WT, wild-type peanut of
Runner genotype; 7 and 11, two independent AtNHX1-expressing peanut lines. Values
are mean ± SD (n = 4). ** statistically significant at P < 0.01.
A
B
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Figure 3.6. Relative amount of chlorophyll present in wild-type and AtNHX1-expressing
peanut plants after 150 mM NaCl treatment. WT, wild-type peanut of Runner genotype; 7
and 11, two independent AtNHX1-expressing peanut lines. Values are mean ± SD (n = 4).
** statistically significant at P < 0.01.
Texas Tech University, Manoj Banjara, August 2010
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3.4. AtNHX1-expressing peanut plants demonstrate higher gas exchange parameters
and biochemical parameters for photosynthesis than wild-type plants under salinity
conditions
Increased growth of AtNHX1-expressing peanut plants compared to wild-type
plants could be the consequence of higher rates of photosynthesis in transgenic plants.
The photosynthetic performance of AtNHX1-expressing peanut plants was analyzed
under normal and salt stress conditions. Net CO2 assimilation rate, stomatal conductance,
and transpiration rate were examined using LI-COR 6400 photosynthesis system. There
were no significant difference in photosynthetic parameters between wild-type peanut
plants and transgenic lines expressing AtNHX1 under normal conditions (data not shown),
while AtNHX1-expressing peanut plants showed better photosynthetic rates (Fig. 3.7A),
stomatal conductance (Fig. 3.7B), and transpiration rates (Fig. 3.7C) under salt conditions.
To study the effects of salinity on photosynthetic parameters, CO2 assimilation
rates (A) with respect to internal CO2 concentrations (Ci) were obtained from AtNHX1-
expressing lines and wild-type plants grown under salt conditions (Table 3.1). For the
estimation of photosynthesis limiting parameters: Vcmax (the maximum rate of
carboxylation by Rubisco) and Jmax (the light-saturated rate of maximum electron
transport), the data from the CO2 response curves were applied to the Photosyn Assistant
software (ver. 1.1.2; Dundee Scientific, UK). Afterward, the characterization of
photosynthesis on wild-type and transgenic plants were performed by employing the data
derived from Photosyn Assistant software to estimate Asat (net photosynthesis at
saturating PPFD), and Amax (photosynthetic capacity at saturating PPFD and saturating
Texas Tech University, Manoj Banjara, August 2010
48
atmospheric CO2). The transgenic peanut lines grown under 150 mM NaCl have
significantly higher Vcmax, Jmax, Asat, and Amax than wild-type plants (Figs. 3.8A, 3.8B,
3.9A, 3.9B). Higher Vcmax of AtNHX1-expressing peanut plants indicates that at low CO2
photosynthesis of transgenic lines were less limited by the Rubisco activity than the wild-
type plants. Similarly, at high Ci, photosynthesis of transgenic lines were less limited by
the rate of regeneration of CO2 acceptor and RuBP compared to wild-type plants.
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Figure 3.7. Gas-exchange performance of wild-type and AtNHX1-expressing peanut
plants after 150 mM NaCl treatment. A. Photosynthesis rate measurement. B. Stomatal
conductance measurement. C. Transpiration rate measurement. WT, wild-type peanut of
Runner genotype; 7 and 11, two independent AtNHX1-expressing peanut lines. Values
are mean ± SD (n = 4). ** statistically significant at P < 0.01.
A
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Figure 3.7. Continued
B
C
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Table 3.1. CO2 assimilation rate (A) with respect to internal CO2 concentration (Ci) of
wild-type and AtNHX1-expressing peanut plants after 150 mM NaCl treatment. 7 and 11,
two independent AtNHX1-expressing peanut lines. Values are mean ± SD (n = 3).
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Figure 3.8. Estimation of photosynthetic parameters for wild-type and AtNHX1-
expressing peanut plants after 150 mM NaCl treatment. A. Maximum carboxylation rate
by Rubisco (Vcmax). B. Light-saturated rate of maximum electron transport (Jmax). WT,
wild-type peanut of Runner genotype; 7 and 11, two independent AtNHX1-expressing
peanut lines. Values are mean ± SD (n = 3). ** statistically significant at P < 0.01; *
statistically significant at P < 0.05.
A
B
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Figure 3.9. Estimation of photosynthetic characteristics for wild-type and AtNHX1-
expressing peanut plants after 150 mM NaCl treatment. A. CO2 saturated photosynthesis
(Asat). B. Maximum potential photosynthesis (Amax). WT, wild-type peanut of Runner
genotype; 7 and 11, two independent AtNHX1-expressing peanut lines. Values are mean
± SD (n = 3). ** statistically significant at P < 0.01; * statistically significant at P < 0.05.
A
B
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CHAPTER IV
DISCUSSION
Drought and salinity are two major environmental stresses that affect the net yield
of various crops. Also, increasing population and warming environment are rising the
demand of agricultural productivity. Thus, it is necessary to generate salt and drought
tolerant crops to meet the increasing food demand. Along with traditional breeding
strategies, genetic engineering technologies can be employed to improve crops yield and
quality. The advancement in plant biotechnology made it possible to identify genes that
might be valuable in crops improvement (Wang et al., 2003; Chinnusamy et al., 2004)
and can be employed on the crop of our interest. AtNHX1 is one such gene, which allows
plant to grow under the salt conditions (Apse et al., 1999; Zhang and Blumwald, 2001;
Zhang et al., 2001; He et al., 2005; Duan et al., 2009; Tian et al., 2006; Xu et al., 2009).
Our lab has successfully expressed Arabidopsis genes AtNHX1 and AVP1 in
cotton plants, which are significantly tolerant to saline and water deficit conditions than
wild-type plants (He et al., 2005; Pasapula et al., 2010). The main objective of this
project is to express the same Arabidopsis gene AtNHX1 in peanut to improve peanut's
salt tolerance. Eighty independent transgenic lines of peanut expressing AtNHX1 were
generated by using Agrobacterium-mediated transformation technique. PCR analysis of
the genomic DNAs of transformed plants were used to confirm the incorporation of
AtNHX1 in the genome of peanut plants (Fig. 3.1). Also, RNA blot analysis was
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55
performed to detect AtNHX1 transcript in peanut lines (Fig. 3.2). Transgenic lines with
high intensity bands in RNA blot assay showed better growth in greenhouse under salt
conditions.
Improved biomass production of AtNHX1-expressing transgenic lines than wild-
type peanut plants in 150 mM NaCl at greenhouse (Figs. 3.3 to 3.5) indicates that
AtNHX1-expressing peanut plants may produce better yield under salt conditions. When
plants expressing large number of vacuolar Na+/H
+ antiporters were grown under saline
conditions, their leaves contain also large amount of sodium ions due to the accumulation
of Na+ in vacuole to alleviate the toxic effect of Na
+ in cytosol, which is accountable for
better photosynthetic capacity (Zhang and Blumwald, 2001; Zhang et al., 2001) (Fig.
3.6A). The data we obtained are consistent with those obtained from Arabidopsis,
rapeseed, tomato, cotton, tobacco, tall fescue, and Petunia hybrid (Apse et al., 1999;
Zhang and Blumwald, 2001; Zhang et al., 2001; He et al., 2005; Duan et al., 2009; Tian
et al., 2006; Xu et al., 2009), which confirms our prediction of generating salt tolerant
peanut plants with the expression of AtNHX1.
The leaf area and leaf number of AtNHX1-expressing peanut plants are larger than
that of wild-type plants (data not shown). In addition to the increased photosynthetic
surface area, transgenic lines had high chlorophyll content than wild-type plants under
the salt conditions (Fig. 3.7), which determines the nitrogen availability in plant (Evans,
1983). Therefore, we can consider that the higher amount of biomass produced by
AtNHX1-expressing plants is due to the multiple effects of large photosynthetic surface
area, better photosynthetic rate, and higher chlorophyll content.
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56
While A was measured with noted Ci values, A for AtNHX1-expressing peanut
plants had greater improvement than wild-type plants grown at 150 mM NaCl (Fig. 3.8).
Carboxylation efficiency by Rubisco and electron transport rate are two photosynthetic
characteristics, which were enhanced for the AtNHX1-expressing plants at low and high
CO2 respectively (Fig. 3.9A & 3.9B). Also, transgenic lines of peanut showed improved
photosynthesis at saturated light and saturated CO2 than wild-type plants under salt
stressed conditions (Fig. 3.10A & 3.10B).
Molecular and physiological data proved our hypothesis that expression of
AtNHX1 in peanut can indeed improve salt tolerance as it did in native Arabidopsis
system (Apse et al., 1999) or heterologous systems such as tomato, rapeseed, cotton,
tobacco, tall fescue, and Petunia hybrida systems (Zhang and Blumwald, 2001; Zhang et
al., 2001; He et al., 2005; Duan et al., 2009; Tian et al., 2006; Xu et al., 2009).
PEG generated by native proton pumps: vacuolar ATPase and PPase are
responsible to energize the highly expressed AtNHX1 to function properly in native and
heterologous systems. Therefore, PEG is the determining factor to limit salt tolerance of
AtNHX1-expressing peanut plants around 150 mM NaCl.
As mentioned earlier, our lab has created salinity and drought tolerant cotton
plants expressing another Arabidopsis gene AVP1 that encodes an H+ pump on vacuolar
membrane (Pasapula et al., 2010), where increased H+ pump activity leads to the increase
in PEG that potentially activates AtNHX1 on the vacuolar membrane to improve the
level of salt tolerance. Thus, double overexpression of AtNHX1 and AVP1 in cotton
generate significantly more salt and drought tolerance than the single expression
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57
(unpublished Data). We could employ this idea to generate peanut plants suitable for the
low water containing soil of West Texas.
4.1. Challenges of Agrobacerium-mediated transformation in peanut
There are still quite a few challenges in the Agrobacterium-mediated
transformation in peanut. For example, low recovery of transformants, lack of efficient
and precise screening procedure, and lack of enough molecular knowledge are a few of
them existing in peanut transformation protocol. As reported previously, explants were
inoculated in the medium without selective antibiotics for 15 days to enhance
transformation efficiency (Nehra et al., 1990). Kanamycin selection was beneficial in
generating transgenic plants from cotolydon explant, even if we apply kanamycin after 2
weeks of cocultivation, but it could be the likely reason for the very low recovery of
transformants (Mathews et al., 1995; Sharma and Anjaiah, 2000).
Cultivated peanut is a tetraploid, although wild relatives are diploid. It is thought
to be evolved relatively recently through a single hybridization event between the
unreduced gametes of two diploid species (Kochert et al., 1996). Thus, nuclear genome
of cultivated peanut is very large, approximately 3 billion base pairs with short gene-rich
genomic sequences. The large non-expressing genomic region increases the probability
of integrating foreign gene into non-transcribing heterochromatin region, which could be
an another basis for the low recovery of transformants. Also, this could be a potential
factor behind low AtNHX1-expression level (Fig. 3.2).
Texas Tech University, Manoj Banjara, August 2010
58
Although 100 µg/ml kanamycin was useful for the selection of transgenic plants
from cotyledon explants, screening of transgenic lines is a potential problem since
kanamycin at high levels of 200 µg/ml restricted but did not always completely inhibited
the regeneration of plant from control wild-type seeds (Sharma and Anjaiah, 2000). Thus,
an efficient screening method for the selection of transgenic peanut is yet to develop.
This problem can be addressed through the modification of selection marker in the
overexpression vector.
It is believed that more than 90% of peanut sequences have close proximity with
the most other plants (Bennetzen, 2000). Genomic sequence analysis revealed that peanut
genome shares more similarity with other plants including Arabidopsis thaliana with 26.7%
sequence similarity (Jayashree et al., 2005). This could be the reason behind the existence
of weak band in wild-type peanut on RNA blot analysis (Fig. 3.2).
If we can overcome the problems that I listed above and come up with a better
protocol in transforming peanut, we will be able to efficiently create more transgenic
peanut lines with various agronomic traits that better suit the tropical and sub-tropical
region of the world including West Texas. Then our goal in creating drought tolerant and
salt tolerant peanut will be realized soon.
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