Abstract
Background and aims
The endophytic fungus Epichloë bromicola forms mutualistic symbiotic associations with wild barley (Hordeum brevisubulatum) in the saline-alkali areas of northwestern China. E. bromicola enhances the tolerance of H. brevisubulatum to salt stress. Because plant polyamine metabolism is closely related to microbial infection and tolerance to diverse abiotic stresses, we hypothesized that in symbiotic plants polyamine modification may result from E. bromicola infection, and that improved tolerance to abiotic stress by the presence of this endophyte might be related to polyamine modification. Our focus in this study was to investigate whether E. bromicola affects polyamine metabolism in host plants under salt stress.
Methods
E. bromicola infected (E+) and endophyte free (E-) wild barley plants were subjected to NaCl treatments (0, 100, 200 and 300 mM). Dry weight, diamine putrescine (Put), triamine spermidine (Spd) and tetramine spermine (Spm) content and the content of their free, soluble conjugated and insoluble bound forms were measured after 21 d exposure to stress.
Results
E. bromicola infection led to significant amelioration of salt stress in H. brevisubulatum. The presence of the endophyte significantly increased dry weight, spermidine and spermine content, but decreased putrescine content and the putrescine: (spermidine + spermine) ratio. E. bromicola infection also lowered the proportion of putrescine in total polyamines, but increased the proportion of spermidine and spermine in total polyamines. Furthermore, E. bromicola infection significantly increased the proportion of insoluble bound forms of polyamines, and decreased the proportion of free forms of polyamines and soluble conjugated forms of polyamines.
Conclusions
H. brevisubulatum salinity stress tolerance induced by E. bromicola infection correlated with enhanced conversion of putrescine to spermidine and spermine, as well as improved shift ability from free forms and soluble conjugated forms of polyamines to insoluble bound forms of polyamines.
Similar content being viewed by others
Explore related subjects
Discover the latest articles, news and stories from top researchers in related subjects.Avoid common mistakes on your manuscript.
Introduction
Salinity is a most persistent and ever-increasing problem in many arid and semi-arid ecosystems of the world (Omar et al. 2009). Salinity stress reduces growth and changes performance and morphology of plants by a multitude of mechanisms including water deficiency, ion toxicity, hormonal imbalance, reactive oxygen toxicity, and nutritional imbalance which may cause membrane destabilization (Flowers 2004; Omar et al. 2009). To combat this toxicity, plant cells synthesize some metabolites, and activate some salt stress related genes and proteins (Roy et al. 2014). Among these classes of metabolites, polyamines are one of the most effective against salinity stress (Groppa and Benavides 2008).
Polyamines are small aliphatic nitrogen compounds that are present in free, soluble conjugated (covalently conjugated with small molecules such as phenolic acids) or insoluble bound forms (bound with macromolecules such as proteins, DNA and RNA). Diamine putrescine (Put), triamine spermidine (Spd) and tetramine spermine (Spm) are three of the most abundant and widespread naturally occurring polyamines. These polyamines are ubiquitous in a wide range of organisms from animals to plants and microbes (Alcázar et al. 2006; Groppa and Benavides 2008). In plants, polyamines influence several physiological processes, including ion channels, antioxidant systems, photosynthesis and nutrient transport systems (Ioannidis et al. 2012; Saha et al. 2015), but not always with the same specificity and efficiency. Changes in polyamine concentrations are essential for regulation of polyamine signaling systems during abiotic stress, including balance between polyamine synthesis and polyamine catabolism, balance with plant hormones, and balance between antioxidant functions and reactive oxygen species (ROS) production (Pál et al. 2015). The biosynthesis and degradation pathways and key enzymes of polyamine metabolism have been well characterized (Duan et al. 2008; Fu et al. 2016; Groppa and Benavides 2008; Kusano et al. 2008; Pál et al. 2015), and polyamines in plants are dynamic and undergo rapid inter-conversion in the polyamine cycle (Fig. 1).
Many studies have shown that plant polyamine metabolism is implicated in inducing tolerance under a wide range of abiotic stresses, including salinity, drought, extreme environmental temperature, heavy metals, ultraviolet - B radiation, mechanical damage and herbicide treatment (Groppa and Benavides 2008; Kasukabe et al. 2004). For example, salt stress increases the free, soluble conjugated, and total spermine content in sunflower leaf tissues (Mutlu and Bozcuk 2005). Salinity stress caused a significant increase in spermine and spermidine content but lowered putrescine content in seedlings of tomato, pepper, lettuce and broccoli (Zapata et al. 2004). In numerous plants, accumulation of polyamine content resulting from various abiotic stresses often correlates with improvement of plant tolerance. It has also long been known that polyamine metabolism changes in plant cells interacting with pathogenic fungi (Asthir et al. 2004), virus infection (Walters 2003), and plant-mycorrhizal associations (Kytöviita and Sarjala 1997; Walters 2000). For example, brown rust (Puccinia hordei) and powdery mildew (Blumeria graminis f. sp. hordei) infection increased polyamine accumulation in barley (Hordeum vulgare) (Greenland and Lewis 1984; Walters and Wylie 1986). Infection by the fungal pathogens Erysiphe cichoracearum and Alternaria tenuis, and the bacterial pathogen Pseudomonas tabaci resulted in a decreased free putrescine and spermidine content in tobacco leaves, with the greatest reduction in infection by pathogens causing the most severe tissue damage (Edreva 1997). Higher contents of free polyamines were detected in association with Lotus glaber and arbuscular mycorrhiza (Glomus intraradices) compared to non-mycorrhizal Lotus glaber (Sannazzaro et al. 2007). However, research on polyamine metabolism in interactions between microorganisms and plants lags behind other research regarding plant polyamines. The available data demonstrates that the nature of polyamine changes depends upon the microbe, plant part involved, and the nature of the plant-microorganism interaction with the host (i.e., mutualistic or parasitic).
Species of the fungal genus Epichloë (formerly Neotyphodium) are a group of biotrophic endophyte that form symbioses with temperate grasses in the subfamily Pooideae (Hettiarachchige et al. 2015; Schardl et al. 2013); they live asymptomatically and intercellularly within the above-ground parts of the host, and roots are not colonized by the fungal endophyte. Epichloë endophyte are present in embryos of seeds by virtue of their colonization of reproductive tissues of the parent plant. The growth of the fungal endophyte is fully synchronized with that of host grasses, beginning with growth of the fungus into embryos upon seed germination, and hyphal colonization of leaves as leaves are developing. When leaf growth stops, hyphal growth ceases but hyphae remain metabolically active for the life of the leaf (Christensen et al. 2008). Some species of Epichloë are vertically transmitted via the mother plant lineage to the seeds. This type of spread is clonal and asexual, resulting in the same endophyte genotype being transmitted to seeds. Other Epichloë species are sexual, developing an external stroma that encloses and inhibits inflorescence development, causing the condition referred to as “choke disease”. Reproductive spores (ascospores) released from stromata can infect other healthy grasses of the same species, and thus are horizontally transmitted (Christensen et al. 2008; Leuchtmann et al. 2014; Saikkonen et al. 2013; Saikkonen et al. 2004; Soto-Barajas et al. 2016). Most Epichloë species are host specific and most of the asexual species are confined to a single host grass (Ekanayake et al. 2012; Gundel et al. 2012).
Many studies have shown that Epichloë endophyte play a role in enhancing tolerance of the grass host to stresses such as high soil saline content (Reza and Mirlohi 2010; Song et al. 2015a), drought (Malinowski and Belesky 2000; Oberhofer et al. 2014), high soil heavy metal content (Monnet et al. 2001; Zhang et al. 2010), insects (Kuldau and Bacon 2008) and disease (Iannone et al. 2017; Ma et al. 2015; Xia et al. 2015). Epichloë endophyte-mediated stress protection is often associated with increased nutrient absorption and secondary metabolites. For example, specific fungal secondary metabolites, such as loline alkaloids produced by some Epichloë endophyte, affect osmotic potential and reduce the effects of drought stress (Kuldau and Bacon 2008). Epichloë endophyte involved in nutrient absorption and ionic balance adjustment increase the competitive ability of the host plant under salinity stress (Reza and Mirlohi 2010; Song et al. 2015a). Although improvements in stress tolerance of host grasses infected by Epichloë endophyte are well known, there has been limited study of the effects of Epichloë infection on host-produced secondary metabolites. It seems likely that presence and metabolic activity of Epichloë endophyte may substantially contribute to or alter metabolic activities of the host.
To our knowledge, there is a paucity of research on involvement of polyamine metabolism in Epichloë endophyte-host plant interactions subjected to abiotic stress. We hypothesized that improved tolerance to abiotic stress by Epichloë infection might be related to polyamine modification, and this may be a remediating mechanism of Epichloë endophyte. Therefore, in this work we aimed to investigate whether the presence of an Epichloë endophyte affects polyamine metabolism in host plants under salt stress, and whether the protective role to host plants was associated with polyamine metabolism.
Wild barley (Hordeum brevisubulatum) is an important forage grass that is widely adaptable to a variety of stress conditions, including salt, alkali and water stresses, and for this reason, H. brevisubulatum is often used as a model plant in studies on salinity (Wang et al. 2016). In addition, the asexual Epichloë endophyte E. bromicola is present in the majority of H. brevisubulatum plants with infection frequencies ranging from 80% to 90% in the saline-alkali areas of Linze county, Gansu province, China (Song et al. 2015b; Chen et al. 2018). It has been reported that E. bromicola plays an important role in improving wild barley salt stress by adjusting ionic homeostasis and modifying nutrient stoichiometry (Song et al. 2015a). Furthermore, many studies have shown the existence of links between polyamine metabolism and redox homeostasis (Gupta et al. 2013), ion homeostasis (Yamasaki and Cohen 2006) and nutrient uptake and transport (Tytti and Seppo 2002). For this reason, H. brevisubulatum was selected as test material for this study. In this study we examined changes in content of three kinds of polyamines (putrescine (Put), spermidine (Spd) and spermine (Spm)) and their presence in various forms (free, soluble conjugated or insoluble bound forms) to gain insights as to whether polyamines are the mechanism by which the systemic Epichloë endophyte enhances growth of H. brevisubulatum in high salinity environments.
Materials and methods
Plant material
Mature reproductive tillers of H. brevisubulatum plants were collected from natural populations on property of the Linze Experimental Station (Lanzhou University, Gansu province, China). Epichloë endophyte infection status was then determined by microscopic examination using the aniline blue staining method and PCR using Epichloë specific primers (tub2-exon 4u-2: GTTTCGTCCGAGTTCTCGAC, tub2-exon 1d-1: GAGAAAATGCGTGAGATTGT) (Moon et al. 2002). The PCR analyses were performed in a total volume of 25 μl (12 μl 2 × Taq MasterMix (ComWin Biotech Corp., Ltd., Beijing, China), 10 μl double-distilled H2O, 1 μl DNA (50 ng/μl), 1 μl target-specific forward primer (10 μM) and 1 μl target-specific reverse primer (10 μM)). The cycling condition used to amplify tub2 were an initial denaturation step for 5 min at 94 o C, 30 cycles of denaturation at 94 o C for 30 s, annealing at 45 o C for 1 min, extension at 72 o C for 1 min, followed by a final synthesis step at 72 o C for 10 min. Products were analysed by gel electrophoresis on a 1.5% agarose gel in 1 × TAE buffer. The DNA fragments were stained with Gold View (Solarbio Corp., Beijing, China) and viewed by UV transillumination. As positive controls, we used E. bromicola WBE1 isolated from H. brevisubulatum. Epichloë-free H. brevisubulatum were served as the negative control.
In order to acquire genetically comparable endophyte infected (E+) and endophyte free (E-) H. brevisubulatum seeds, seeds from one E. bromicola infected mature ear were separated into two equal parts: one part was treated for 1.5 h with a 100 times dilution of 70% Thiophanate-Methyl (Jiangsu Rotam Chemistry Co. Ltd., Jiangsu, China) to kill the Epichloë endophyte, and then was rinsed with water to remove attached fungicide; the other part was treated with distilled water. Fungicide treated (E-) and untreated (E+) seeds were then planted in vermiculite that had been sterilized in an oven at 150 o C for 24 h. All plants were irrigated with water and 1/2 strength Hoagland nutrient solution. Clones of E+ and E- plants were clipped to 5 cm above the soil line; each plant was clonally propagated resulting in numerous plantlets. Seeds were collected from these E+ and E- tillers and the endophyte infection status was monitored again by microscopic examination and PCR using Epichloë specific primers as described above. By this means, we obtained two genetically similar populations of H. brevisubulatum that differed only in the absence (E-) or presence (E+) of the E. bromicola. All acquired seeds were stored at 4 o C to maintain endophyte viability. During the experiment, plants were examined several times using the aniline blue staining method of the absence or presence of E. bromicola.
Experimental design
Seeds harvested from E+ and E- plants were sown into two trays (one tray for E+ and one tray for E-) containing heat-sterilized (150 o C for 24 h) vermiculite and irrigated with water as required. After 2 weeks, seedlings were transplanted into black plastic rectangular containers (15 cm × 8 cm × 5 cm) with six seedlings per container, with each container filled with 2 L of 1/2 strength Hoagland nutrient solution. The nutrient solution was renewed every three days to avoid ion nutrient imbalance.
After 7 d, NaCl (0 mM, 100 mM, 200 mM and 300 mM) was gradually applied in nutrient solutions and replicated three times (3 containers) in a randomized complete block design. In order to avoid salt shock, plants were treated with 50 mM salt for the first day and 100 mM salt for the second day, and the full concentration of each treatment was applied from day 3 onwards. During the stress experiment, solutions in each container were renewed every three days to ensure that a constant NaCl concentration was maintained. In addition, the position of each container in the block was changed randomly every 3 days to reduce positional effects. After 21 d exposure to NaCl stress, plants were harvested for analysis, and carefully rinsed with distilled water to remove the NaCl and nutrient solution from the surface of the plants. Some of plants were frozen in liquid nitrogen in order to measure polyamines, and some plants were oven-dried at 80 o C to a constant weight to determine dry weight. Plant material was also collected before the salt stress for polyamines analyses to assess pre-experiment levels (show as W0 in the figure legend). During the experiment, the nutrient solutions in the container were aerated by an air pump for 30 min at 6-h intervals. Greenhouse conditions were maintained at a temperature of 28 o C/25 o C (day/night) and a photoperiod of 16/8 h (light/dark; the flux density was about 800 μmol m−2 s−1), with an approximate relative humidity of 65%.
Polyamine (PA) analyses
Three kinds of polyamine: diamine putrescine, triamine spermidine and tetramine spermine contents and their free, soluble conjugated and insoluble bound forms contents were measured (Fig. 1).
Polyamines were extracted and measured using the methods of Hu et al. (2012): briefly, approximately 1.0 g of fresh leaf blade material was homogenized with 4 mL of 5% (v/v) cold perchloric acid with a mortar and pestle, and the ground material was incubated at 4 o C for 60 min, then 1,6-hexanediamine (an internal standard) was added to the homogenate. The mixture was then centrifuged at 12,000×g for 30 min at 4 o C for clarification. The supernatant was either used to measure free polyamine concentrations or further hydrolyzed to determine soluble conjugated polyamines. For supernatant hydrolysis, 1 ml of perchloric acid extract (supernatant) was mixed with 5 ml of 6 N hydrochloric acid and hydrolyzed at 110 o C for 18 h in a reagent bottle. After acid hydrolysis, the hydrochloric acid was evaporated at 70 o C, and the residue dissolved with 2 ml of 5% (v/v) perchloric acid. The mixture (acid-soluble polyamines fraction containing free and soluble conjugated polyamines) was then centrifuged at 12,000×g for 30 min at 4 o C. To acquire insoluble bound polyamines forms, the precipitate was washed several times with 5% (v/v) perchloric acid to remove any residue of soluble polyamines and then the precipitate was suspended in 5 ml of 6 N hydrochloric acid. This solution was then hydrolyzed using the method described above.
Polyamines acquired from the non-hydrolyzed supernatant (free form), hydrolyzed supernatant (free and soluble conjugated form), and the precipitate (insoluble bound form) were then benzoylated as follows: 1 ml of the supernatant was treated with 2 ml of 2 N sodium hydroxide and 15 μl of benzoyl chloride, incubated for 30 min at 37 o C after mixing vigorously, then the reaction was terminated by adding 4 ml of saturated sodium chloride solution. Thereafter, the benzoyl polyamines were extracted with 3 ml cold diethyl ether, then 1.5 ml of the diethyl ether phase was evaporated, finally the residuum was redissolved in 1 ml methanol.
Polyamines were quantified using Agilent 1100 high-performance liquid chromatography, with an Agilent 250 mm × 4.6 mm reverse-phase C18 column. Eluents used were 64% (v/v) methanol at a flow rate of 1 ml min−1, and column temperature was maintained at 25 o C. A fixed-wavelength UV detector (G1314, VWD, Agilent) at 254 nm was used to detect polyamine peaks, and 20 μl of benzoyl samples were identified and quantified by comparison with external standard curves. The polyamine standards used were purchased from Sigma-Aldrich Company (China).
Soluble conjugated polyamine contents were calculated by the subtraction of the free polyamine concentration from the acid-soluble polyamine concentration, and polyamine concentrations were expressed as nmol/g fresh weight.
Statistical analysis
Data were analyzed by SPSS statistical software (Ver. 19.0, SPSS, Inc., Chicago, IL, USA). Two-way analysis of variance was used to determine the effects of endophyte (E) and salt stress (S) on three kinds of polyamines, the proportion of putrescine, spermidine and spermine in the total polyamines, the proportion of free form, soluble conjugated form and insoluble bound form polyamines in the total polyamines and putrescine: (spermidine + spermine) ratios. Significance of difference tests between E+ and E- plants under the same salt concentration stress in all of the parameters were carried out by independent T-test, and significant difference between different salt concentrations in all of the parameters were carried out using Duncan’s test at P < 0.05. All data were presented as mean ± standard errors.
Results
Plant dry weights
After treatment with three concentrations of NaCl for 21 d, the differences between E+ and E- plants under the high NaCl concentration (300 mM) were evident. The results showed that compared with the control treatment (0 mM), the dry weight of plants decreased as the salt concentrations increased (Fig. 2), and endophyte infection significantly positively influenced plant dry weight especially under the higher salt concentration but not under the control (Fig. 2). We can conclude that the presence of endophyte on H. brevisubulatum led to amelioration of salt stress.
Putrescine content
Salt stress positively affected the free form, insoluble bound form and total putrescine content of H. brevisubulatum plants (Fig. 3a, c, d, Table 1), while having no effects on the soluble conjugated form of putrescine (Fig. 3b, Table 1). The presence of endophyte significantly decreased each form and total putrescine content at higher salt concentration treatments. The difference between the E+ and E- plants became larger as the salt concentrations increased, while they showed no significant difference under the control and low salinity conditions (100 mM) (Fig. 3).
Spermidine content
Irrespective of endophyte infection, the insoluble bound form and total spermidine content of plants increased at first and then declined as the salt concentrations increased (Fig. 4c, d), while soluble conjugated spermidine content increased gradually with increasing stress levels (Fig. 4b), however, the effects of salt stress on free form spermidine content was not significant (Fig. 4a, Table 1). Endophyte infection strengthened the increase of the insoluble bound form and the total spermidine content under 100 and 200 mM stress, but alleviated the decrease under the highest salt concentration (300 mM) (Fig. 4c, d). The presence of the endophyte also enhanced the increase of the soluble conjugated form of spermidine (Fig. 4b) but alleviated the decrease of the free form of spermidine under salt stress (Fig. 4a). The E+ plants had higher levels of total and each form of spermidine than E- plants under salt stress (but not under the control) (Fig. 4).
Spermine content
Insoluble bound form and total spermine content showed a gradually increasing trend with increasing salt concentrations (Fig. 5c, d), but free form spermine content decreased at 100 and 200 mM salt stress and then showed a sharp increase under the 300 mM salt stress (Fig. 5a). Soluble conjugated spermine content showed an increasing trend under 100 and 200 mM salt condition compared to control and then sharply decreased under the 300 mM salt stress (Fig. 5b). Endophyte infection significantly increased the soluble conjugated form and the total spermine content under the salinity treatment, and E+ plants had higher conjugated form and higher total spermine content than E- plants within the measured range of salt stress (Fig. 5b, d, Table 1). The insoluble bound form of spermine showed a different pattern, it was significantly lower in E+ plants than in E- plants when exposed to salt stress treatments (Fig. 5c).
The proportion of putrescine, spermidine and spermine in the total polyamines
Total polyamine content including putrescine, spermidine and spermine was analyzed, and found to decrease as a consequence of endophyte infection. Differences between E+ and E- plants became larger with increasing salt concentration. E- plants had higher total polyamine content than E+ plants at 200 and 300 mM salt (Fig. 6a). However, due to significantly higher levels of putrescine than spermidine or spermine in H. brevisubulatum plants (Fig. 3d, 4d and 5d), even though E+ plants had higher spermidine and spermine content under salt stress, total polyamine content was higher in E- plants (Fig. 6a). The results showed that the proportion of putrescine content in total polyamines of E+ plants was significantly lower than of E- plants at the higher stress levels (Fig. 6b); the proportion of spermidine and the proportion of spermine in total polyamine content showed an opposite pattern, they were higher in E+ plants than in E- plants under salt stress treatment (Fig. 6c, d). From these results, we can conclude that endophyte infection enhanced the conversion ability of H. brevisubulatum from putrescine to spermidine and spermine in the saline environment (Fig. 6, Table 2).
The proportion of free form, soluble conjugated form and insoluble bound form polyamines in the total polyamines
Irrespective of the presence of endophyte, the proportion of free form and the proportion of soluble conjugated form polyamines in total polyamines showed a decreasing trend under salt stress (Fig. 7a, b), but the proportion of insoluble bound form polyamines in total polyamines showed a different pattern, being significantly increased in the 200 and 300 mM salt treatments (Fig. 7c). Endophyte infection reduced the proportion of free form and the proportion of soluble conjugated form polyamines in total polyamines; polyamines were lower in E+ plants than in E- plants under higher salt concentration treatments (Fig. 7a, b), but the presence of endophyte strengthened the increase of the proportion of insoluble bound polyamines in total polyamines when exposed to salt treatments, with the difference between E+ and E- plants being significant (P < 0.05) at 200 and 300 mM salt (Fig. 7c). These results indicate that endophyte infection improved the shift ability of H. brevisubulatum from free form and soluble conjugated form polyamines to insoluble bound form polyamines under salt stress (Fig. 7, Table 3).
Putrescine: (spermidine + spermine) ratio
The insoluble bound form and total putrescine: (spermidine + spermine) ratio showed a sharp increase under the 300 mM salt stress (Fig. 8c, d), while the soluble conjugated form putrescine: (spermidine + spermine) ratio declined as the salt stress increased (Fig. 8b). However, salt stress had no effects on the free form putrescine: (spermidine + spermine) ratio (Fig. 8a, Table 4). Endophyte infection lowered each form and total putrescine: (spermidine + spermine) ratios; they were significantly higher in E- plants than in E+ plants especially under higher salt stress concentrations (Fig. 8). Endophyte infection increased spermidine and spermine content but lowered putrescine content in the high salt treatment.
Discussion
Understanding the mechanism by which infection by the Epichloë endophyte enhance the tolerance of grass plants to biotic and abiotic stresses is essential for improvement and persistence of host plants for a range of applications, e.g., breeding of new varieties for arid areas and cultivating plants in high salinity areas for soil conservation and improvement. High salinity poses threats to agricultural sustainability, and causes adverse damage to plant growth and productivity. Our results indicate that E. bromicola-infected H. brevisubulatum plants are better adapted to high salt soils than the genetically identical endophyte-free plants. E. bromicola infected H. brevisubulatum outperformed uninfected plants only under salt stress, and the differences were usually more apparent at the higher stress conditions, whereas no significant differences were observed in non-stressed plants. Similar results were also found by Saikkonen et al. (2006), Song et al. (2015a) and Xia et al. (2015). We infer that adverse conditions (e.g., excessive Na+ injury, osmotic stress) may increase the benefit of Epichloë endophyte to the grass.
Polyamine changes due to microbe infection (biotic stress)
Plant polyamine metabolism undergoes changes in response to microbe infection, and the change pattern depends on the relationship (mutualistic or antagonistic) of the microbe to its host plant. Our results with H. brevisubulatum plants containing E. bromicola suggest that metabolism of polyamines is correlated with mutualistic Epichloë endophyte infection and abiotic stress. Endophyte-originated and/or host-originated polyamines may have positive effects on growth of H. brevisubulatum exposed to salt stress. In antagonistic host-pathogen interactions, polyamines relate to pathogen recognition and defense activation, and are accompanied by hypersensitive responses. Conjugated polyamines exhibit antimicrobial properties and contribute to the defensive systems of plants against pathogenic microorganisms (Pál et al. 2011). Hydrogen peroxide derived from polyamine catabolism contributed to reactive oxygen species generation resulting in hypersensitive cell death during the hypersensitive response (Yamaguchi and Sano 2003). There are also several studies that have shown that polyamines act as regulatory factors in plant-arbuscular mycorrhizal fungus interactions; they act in the molecular signaling events between the symbiosis partners (Ghachtouli et al. 1996; Parádi et al. 2003; Smith et al. 1998). Although it is the roots of host grasses that are exposed to the salinity conditions, there are no hyphae in roots of Epichloë endophyte infected plants. The changes in root functions of nutrient uptake in Epichloë endophyte-grass associations are probably regulated through signals induced by the fungus. Polyamines have been shown to interconnect with hormones (namely auxins, abscisic acid, gibberellins and cytokinins), and reactive oxygen species (ROS) and nitric oxide (NO) to form a complex signaling network (Tiburcio et al. 2014). For example, polyamines can induce NO production, which serves as a signal that induces salt tolerance by decreasing the Na+ to K+ ratio through stimulation of gene expression of tonoplast Na+/H+ antiporter and plasma membrane H+-ATPase (Yamasaki and Cohen 2006). It has been also suggested that polyamine induced NO production could be remediated by the polyamine oxidation reaction product H2O2 (Wimalasekera et al. 2011). This may indicate that E. bromicola -induced polyamine metabolism may mediate the action of plant signaling molecules that regulate mechanisms and adaptation processes of salt stress tolerance in H. brevisubulatum and ensure a better survival than endophyte-free conspecifics. However, to better understand the intrinsic mechanisms underlying crosstalk between polyamines, plant hormones and signal molecules, further detailed study will be needed in this area.
Polyamine changes due to abiotic stress
Rapid change in levels of polyamines in response to abiotic stress suggests that polyamines function in alleviation of stress. In our experiment, irrespective of endophyte infection, stress-induced changes in putrescine, spermidine and spermine content occurred under salinity conditions despite being followed by a decrease after its peak value in spermidine content. E+ plants, which showed more salt-tolerance, accumulated higher spermidine and spermine content, but lower putrescine content, than E- plants. Similar results were found in other studies. For example, sensitivity to salt-stress Solanum species was also reported to be associated with an increase in putrescine content and an apparent impairment in the capacity to shift putrescine to spermidine (Santa-Cruz et al. 1997). And according to Krishnamurthy and Bhagwat (1989), salt-tolerant rice cultivars accumulated more spermidine and spermine resulting in improved levels of total polyamines, with a relative decrease of putrescine content. However, differences in polyamine responses to salinity stress have been observed among and within species. For example, Prakash and Prathapasenan (1988) reported that endogenous content of polyamines decreased in rice seedlings under salinity stress. In tomato, salinity treatment decreased the content of putrescine and spermidine in both salt-tolerant and salt-sensitive lines. The spermine content greatly decreased in salt-sensitive lines over the salinization period, however, it did not decrease with salt stress in salt-tolerant lines (Santa-Cruz et al. 1997). Owing to the reduction of chlorophyll breakdown and the stabilization of membrane systems either by inhibiting phospholipid trans-bilayer movement (Bratton 1994) or by stabilizing molecular complexes of thylakoid membranes (Besford et al. 1993), spermidine and spermine may serve as protectants from stress conditions in plants. Spermidine and spermine also may significantly reduce the leakage of amino acids and electrolytes induced by salinity stress (Chattopadhayay et al. 2002). Putrescine may have different effects than those reported for spermidine and/or spermine since it causes membrane depolarization and increases potassium leakage. Increased levels of putrescine may correlate with reduced plant growth and may increase adverse effects of salinity stress. It has been reported that some plants accumulate higher amounts of endogenous spermidine and spermine as a way to cope with excessive salt stress (Duan et al. 2008; Roychoudhury et al. 2011). Results presented in our study show that Epichloë endophyte infection reduced the accumulation of putrescine and enhanced the increase of spermidine and spermine under salt stress, suggesting a positive role of the Epichloë endophyte in host plant response to salt stress.
Relationship between polyamine and proline under salt stress
Proline is associated with the activation of reactive oxygen species scavenging enzymes during salinity stress; there was a strong correlation between increased level of proline and the capacity to survive under high salinity conditions (Gupta and Huang 2014). Song (2015) reported that salt stress results in accumulation of proline in the same material as in our study; the presence of the Epichloë endophyte enhanced the increase in proline, especially under the higher stress conditions. Previous studies have shown that proline levels are tightly correlated to spermidine content in stressed plants (Smith et al. 1998). Moreover, putrescine catabolism may also contribute to proline; proline and putrescine are connected via the activity of relevant enzyme metabolism as a precursor-product relationship (Aziz et al. 1998). We infer that the impact of the Epichloë endophyte on salt tolerance of host plants is also associated with the interaction between polyamine metabolism and proline content.
Polyamines regulate redox homeostasis under salt stress
Under salt stress, plant cells rapidly accumulate reactive oxygen species (ROS), a response widely known “oxidative burst”. Low levels of ROS (H2O2) function in signal transduction; however, at higher concentrations ROS can lead to nucleic acid damage, membrane lipid peroxidation, protein denaturation, and cell death (Miller et al. 2008). On the other hand, plants produce a diverse set of antioxidants to counteract the potentially detrimental effects of the oxidative burst, such as polyamines, that have antioxidative properties. Polyamines function in redox homeostasis management during plant abiotic stress response by: 1) regulating cellular responses through modulation of ROS homeostasis, 2) activating enzymes and scavenging free radicals, and 3) promoting ROS degradation (Fiscaletti et al. 2013; Gupta et al. 2013). Based on our results, we infer that endophyte-infection modulates polyamine change to promote ROS homeostasis and enhance salt stress tolerance. Our study showed that E+ plants had higher free and soluble conjugated forms of spermidine and spermine. Because free polyamines have the ability to detoxify hydrogen peroxide and superoxide anions, while the soluble conjugated forms are responsible for scavenging other ROS (Kubi 2005), soluble conjugated forms also show higher antioxidant ability than free forms of polyamines (Kuznetsov and Shevyakova 2007); it thus may be inferred that E+ plants had more antioxidant capacity than E- plants. Similar results were found in other studies, for example, previous studies have suggested that Epichloë endophyte can prevent ROS production or induce hosts to more efficiently scavenge ROS to mitigate the adverse effects of abiotic stress (Rodriguez et al. 2008). White Jr. and Torres (2010) suggested that ROS produced by endophyte may enhance antioxidants (for example: phenolics, mannitol, proline) production of symbiotic plants, and thus may protect plants from oxidative stress produced by various biotic and abiotic stresses. Tanaka et al. (2006) demonstrated that for the endophyte E. festucae, ROS production is critical in the mutualistic relationship between fungus and plants.
Polyamines related to mechanisms controlling ion balance and photosynthesis, and regulating nutrient uptake of plants under salt stress
Plant salt stress adaptive responses are also closely related to the ability to control ion transport and ion homeostasis. Studies on the same materials as in our study have shown that Epichloë endophyte infected plants have higher N, P and K+ content, but lower Na+ content, and lower ratios of C:N, C:P, Na+:K+ than in endophyte-free plants (Song et al. 2015a). Together with our results, we can infer that the response of polyamine changes in H. brevisubulatum to E. bromicola infection may be related to mechanisms controlling ion balance and regulating nutrient uptake of plants. Polyamine accumulation in plants requires an osmotic signal and/or the presence of permeable ions, such as sodium and potassium (Erdei et al. 1996; Tytti and Seppo 2002; Zhao et al. 2007). Polyamines are reported to improve salt tolerance through their effects on ion transport, ROS, and affecting intracellular Ca2+ homeostasis by adjusting Ca2+ transport systems in the plasma membranes of root cells (Zepeda-Jazo et al. 2011). For example, polyamines play a role in the improvement of K+/Na+ homeostasis by restricting Na+ influx into roots and by suppressing K+ efflux from shoots (Zhao et al. 2007). Spermine limits Na+ influx and K+ efflux by blocking non-selective cation channels and inward-rectifying K+ channels. Putrescine and spermine reduce hydroxyl radical-induced K+ efflux (Shabala et al. 2007; Zepeda-Jazo et al. 2008). Polyamines enhance membrane stability and interact with plasma membrane phospholipids to affect cation-anion transport (for example: H+- and Ca2+-ATPase transporters) in salinity environment (Pottosin and Shabala 2014). The cumulative effects of hydrogen peroxide and polyamines in response to salinity stress leads to a rapid rise in intracellular Ca2+ content, and causes a positive feedback to ROS production through NADPH-oxidase localized in plasma membranes (Bose et al. 2014). On the other hand, increased intracellular Ca2+ activates non-selective cation channels and inhibits Na+-induced K+ efflux, thus ameliorating the toxicity of Na+ (Shabala et al. 2006). Several studies have also shown the importance of the interaction between polyamines and nutrient uptake of plants, for example, putrescine increases occur under mineral nutrient deficiency. Nitrogen deficiencies accelerated changes in polyamine content, especially in soluble conjugated and insoluble bound forms (Tytti and Seppo 2002). Polyamines also play roles in phosphorus nutrition-dependent regulation of AM symbiosis (Smith et al. 1998), and could also be considered as nitrogen storage to meet the needs of energy during salinity stress (Pál et al. 2015). It has been demonstrated that Epichloë endophyte infection improved photosynthetic rates and transpiration rates under biotic or abiotic stress (Rozpądek et al. 2015; Song 2015; Xia et al. 2016). There are also several lines of evidence supporting the relationship between photosynthesis and polyamines. For example, higher transpiration rate could promote long-distance transport of polyamines from roots to shoots via xylem vessels (Smith et al. 1998). Transglutaminase catalyzes the conjugation of polyamine to photosynthetic compounds, and this may lead to improved photosynthetic ability under stress conditions (Ioannidis et al. 2012). Thus, in E. bromicola infected H. brevisubulatum, the mechanism by which the presence of the endophyte can ameliorate the effects of salt on plants appears to involve changes in polyamines. Modified polyamine metabolism is also related to mechanisms that control photosynthesis, ion homeostasis, nutrient uptake and transport.
How soluble conjugated and insoluble bound polyamines regulate stress tolerance
In our study, E+ plants, which showed more salt tolerance than E- plants, accumulated more soluble conjugated and insoluble bound spermidine, and soluble conjugated spermine, but lower soluble conjugated and insoluble bound putrescine, and lower insoluble bound spermine. A key role for soluble conjugated and insoluble bound polyamines in the regulation of stress tolerance has been proposed; polyamine function is regulated by conjugation reactions through binding and interaction with nucleic acids, proteins or phospholipids (Bouchereau et al. 1999). Conjugated polyamines are preferred substrates for peroxidase; they react with peroxidases and may remove hydrogen peroxide in the apoplast (Negrel and Lherminier 1987); they also regulate interactions between polyamines and inorganic cations such as Ca2+, which relates to the proposed role of polyamines on membrane stabilization (Bouchereau et al. 1999). Enhanced levels of membrane-bound polyamines have been associated with stabilization and maintenance of plasma membranes, mitochondria and tonoplasts, and these appear to be involved in the acclimatization of plants to salinity environments (Hu et al. 2012). Protein-bound polyamines are also involved in photosynthetic functions (Margosiak et al. 1990). However, high levels of putrescine conjugates can contribute to cell multiplication inhibition and cell differentiation suppression, and lead to abnormal floral development in several species (Martin-Tanguy 1997). Previous studies demonstrated that overexpressing the S-adenosylmethioine decarboxylase (SAMDC) gene in tobacco plants lead to an increase in conjugated form polyamines, and transgenic plants exhibited enhanced tolerance to drought and salinity (Waie and Rajam 2003). From above mentioned, it is likely to indicate that enhanced conversion of free form and soluble conjugated form polyamines to insoluble bound form polyamines are related to mechanisms of salt tolerance induced by Epichloë endophyte infection.
The relationship between putrescine: (spermidine + spermine) ratio and stress tolerance
Salinity stress leads to the change in the putrescine: (spermidine + spermine) ratio in plants. Our study revealed that the insoluble bound form and the total putrescine: (spermidine + spermine) ratio increased with salinity, which is consistent with the idea of a protective role of spermidine and spermine against saline stress (Pál et al. 2015). Endophyte infection significantly lowered the putrescine: (spermidine + spermine) ratio, especially under the higher stress levels, which could alleviate salinity damage to host plants. This result suggests a positive role for the endophyte in host plant responses to salt stress. In several systems, an accumulation of spermidine and spermine, but not putrescine, may confer stress tolerance (Zapata et al. 2004). Increased accumulation of putrescine, leading to a higher putrescine: (spermidine + spermine) ratio, may even injure plants. It was found that salt-sensitive plant species accumulate more putrescine than salt-tolerant species. The putrescine: (spermidine + spermine) ratio decreased with salinity increase in salt tolerant tomato species, but not in salt-sensitive species (Santa-Cruz et al. 1997). Furthermore, the primary factors responsible for salinity tolerance are not only elevated levels of spermidine and spermine but also the enhanced turnover, and the ability to accumulate high levels of insoluble bound polyamine.
Conclusions
Our study is the first indication of the possible role of polyamines in the symbiosis between host plant and mutualistic Epichloë species under abiotic stress. Our primary experiments showed that Epichloë endophyte infection resulted in an increase in each form and total spermidine, soluble conjugated form and total spermine, but decreased total putrescine, and insoluble bound form spermine. Epichloë endophyte infection also decreased the putrescine: (spermidine + spermine) ratios. Furthermore, Epichloë endophyte infection significantly increased the proportion of the insoluble bound form polyamine, while lowering the proportion of the free form polyamine and soluble conjugated form polyamine. Based on these results, we conclude that salinity stress tolerance induced by Epichloë endophyte infection correlated with the enhanced conversion of putrescine to spermidine and spermine, as well as an improved shift ability from the free form and the soluble conjugated form polyamine to the insoluble bound form polyamine (Fig. 9).
Based on our observations and reports from Song et al. (2015a), we propose that the change of polyamine metabolism in planta produced by Epichloë endophyte infection positively regulates photosynthesis, ion balance, nutrient stoichiometry and signal transduction. However, the situation may be reverse where polyamine metabolism is affected by some of these physiological characters, thereby preventing excessive adverse damage to H. brevisubulatum growth induced by NaCl. While crosstalk and interplay between polyamine turnover and other physiological systems during salinity stress is complex, it is essential to understand how this system works for its potential in enhancing plant salinity stress tolerance. Besides direct protective roles, polyamines serve as signaling molecules to regulate polyamine-mediated signaling pathways. It is tempting to speculate that improved abiotic stress tolerance induced by Epichloë endophyte is not only related to changed polyamine metabolism but also by signaling processes. In order to fully understand Epichloë endophyte induced polyamine metabolism and the possible mechanisms by which the presence of Epichloë endophyte enhances growth of H. brevisubulatum exposed to salt stress, further research is needed on polyamine-related signaling pathways in H. brevisubulatum, together with other physiological traits including photosynthesis and nutrient transport.
References
Alcázar R, Marco F, Cuevas JC, Patron M, Ferrando A, Carrasco P, Tiburcio AF, Altabella T (2006) Involvement of polyamines in plant response to abiotic stress. Biotechnol Lett 28:1867–1876. https://doi.org/10.1007/s10529-006-9179-3
Asthir B, Spoor W, Duffus CM (2004) Involvement of polyamines, diamine oxidase and polyamine oxidase in resistance of barley to Blumeria graminis f. sp. Hordei. Euphytica 136:307–312. https://doi.org/10.1023/B:EUPH.0000032730.48474.b1
Aziz A, Martin-Tanguy J, Larher F (1998) Stress-induced changes in polyamine and tyramine levels can regulate proline accumulation in tomato leaf discs treated with sodium chloride. Physiol Plant 104:195–202. https://doi.org/10.1034/j.1399-3054.1998.1040207.x
Besford RT, Richardson CM, Campos JL, Tiburcio AF (1993) Effect of polyamines on stabilization of molecular complexes in thylakoid membranes of osmotically stressed oat leaves. Planta 189:201–206. https://doi.org/10.1007/BF00195077
Bose J, Rodrigomoreno A, Shabala S (2014) ROS homeostasis in halophytes in the context of salinity stress tolerance. J Exp Bot 65:1241–1257. https://doi.org/10.1093/jxb/ert430
Bouchereau A, Aziz A, Larher F, Martin-Tanguy J (1999) Polyamines and environmental challenges: recent development. Plant Sci 140:103–125. https://doi.org/10.1016/S0168-9452(98)00218-0
Bratton DL (1994) Polyamine inhibition of transbilayer movement of plasma membrane phospholipids in the erythrocyte ghost. J Biol Chem 269:22517–22523
Chattopadhayay MK, Tiwari BS, Chattopadhyay G, Bose A, Sengupta DN, Ghosh B (2002) Protective role of exogenous polyamines on salinity-stressed rice ( Oryza sativa ) plants. Physiol Plant 116:192–199. https://doi.org/10.1034/j.1399-3054.2002.1160208.x
Chen TX, Simpson WR, Song QY, Chen SH, Li CJ, Ahmad RZ (2018) Identification of Epichloë endophytes associated with wild barley (Hordeum brevisubulatum) and characterisation of their alkaloid biosynthesis. New Zeal J Agr Res. https://doi.org/10.1080/00288233.2018.1461658
Christensen MJ, Bennett RJ, Ansari HA, Koga H, Johnson RD, Bryan GT, Simpson WR, Koolaard JP, Nickless EM, Voisey CR (2008) Epichloë endophytes grow by intercalary hyphal extension in elongating grass leaves. Fungal Genet Biol 45(2):84–93. https://doi.org/10.1016/j.fgb.2007.07.013
Duan J, Li J, Guo S, Kang Y (2008) Exogenous spermidine affects polyamine metabolism in salinity-stressed Cucumis sativus roots and enhances short-term salinity tolerance. J Plant Physiol 165:1620–1635. https://doi.org/10.1016/j.jplph.2007.11.006
Edreva A (1997) Tobacco polyamines as affected by stresses induced by different pathogens. Biol Plant 40:317–320. https://doi.org/10.1023/a:1001093209229
Ekanayake PN, Hand ML, Spangenberg GC, Forster JW, Guthridge KM (2012) Genetic diversity and host specificity of fungal endophyte taxa in fescue pasture grasses. Crop Sci 52:2243–2252. https://doi.org/10.2135/cropsci2011.12.0664
Erdei L, Szegletes Z, Barabás K, Pestenácz A (1996) Responses in polyamine titer under osmotic and salt stress in sorghum and maize seedlings. J Plant Physiol 147:599–603. https://doi.org/10.1016/S0176-1617(96)80052-6
Fiscaletti D, Angeli D, Tarozzi L, Barozzi GS (2013) Plant polyamines in abiotic stress responses. Acta Physiol Plant 35:2015–2036. https://doi.org/10.1016/j.ijheatmasstransfer.2012.11.039
Flowers TJ (2004) Improving crop salt tolerance. J Exp Bot 55:307–319. https://doi.org/10.1093/jxb/erh003
Fu XZ, Huang Y, Xing F, Chun CP, Ling LL, Cao L, Peng LZ (2016) Changes in free polyamines and expression of polyamine metabolic genes under drought and high-temperature in Citrus sinensis. Biol Plant 60:1–6. https://doi.org/10.1007/s10535-016-0636-0
Ghachtouli NE, Martin-Tanguy J, Paynot M, Gianinazzi S (1996) First-report of the inhibition of arbuscular mycorrhizal infection of Pisum sativum by specific and irreversible inhibition of polyamine biosynthesis or by gibberellic acid treatment. FEBS Lett 385:189–192. https://doi.org/10.1016/0014-5793(96)00379-1
Greenland AJ, Lewis DH (1984) Amines in barley leaves infected by brown rust and their possible relevance to formation of 'green islands'. New Phytol 96:283–291. https://doi.org/10.1111/j.1469-8137.1984.tb03565.x
Groppa MD, Benavides MP (2008) Polyamines and abiotic stress: recent advances. Amino Acids 34:35–45. https://doi.org/10.1007/s00726-007-0501-8
Gundel PE, Martínez-Ghersa MA, Omacini M, Cuyeu R, Pagano E, Ríos R, Ghersa CM (2012) Mutualism effectiveness and vertical transmission of symbiotic fungal endophytes in response to host genetic background. Evol Appl 5:838–849. https://doi.org/10.1111/j.1752-4571.2012.00261.x
Gupta B, Huang B (2014) Mechanism of salinity tolerance in plants: physiological, biochemical, and molecular characterization. Int J Genomics 2014:701596. https://doi.org/10.1155/2014/701596
Gupta K, Dey A, Gupta B (2013) Plant polyamines in abiotic stress responses. Acta Physiol Plant 35:2015–2036. https://doi.org/10.1007/s11738-013-1239-4
Hettiarachchige IK, Ekanayake PN, Mann RC, Guthridge KM, Sawbridge TI, Spangenberg GC, Forster JW (2015) Phylogenomics of asexual Epichloë fungal endophytes forming associations with perennial ryegrass. BMC Evol Biol 15:72. https://doi.org/10.1186/s12862-015-0349-6
Hu X, Zhang Y, Shi Y, Zhang Z, Zou Z, Zhang H, Zhao J (2012) Effect of exogenous spermidine on polyamine content and metabolism in tomato exposed to salinity-alkalinity mixed stress. Plant Physiol Biochem 57:200–209. https://doi.org/10.1016/j.plaphy.2012.05.015
Iannone LJ, Vignale MV, Pinget AD, Re A, Cargo PDM, Novas MV (2017) Seed-transmitted Epichloë sp. endophyte alleviates the negative effects of head smut of grasses (Ustilago bullata) on Bromus auleticus. Fungal Ecol 29:45–51. https://doi.org/10.1016/j.funeco.2017.06.001
Ioannidis NE, Cruz JA, Kotzabasis K, Kramer DM (2012) Evidence that putrescine modulates the higher plant photosynthetic proton circuit. PLoS One 7:e29864. https://doi.org/10.1371/journal.pone.0029864
Kasukabe Y, He L, Nada K, Misawa S, Ihara I, Tachibana S (2004) Overexpression of spermidine synthase enhances tolerance to multiple environmental stresses and up-regulates the expression of various stress-regulated genes in transgenic Arabidopsis thaliana. Plant Cell Physiol 45:712–722. https://doi.org/10.1093/pcp/pch083
Krishnamurthy R, Bhagwat KA (1989) Polyamines as modulators of salt tolerance in rice cultivars. Plant Physiol 91:500–504. https://doi.org/10.1104/pp.91.2.500
Kubi J (2005) The effect of exogenous spermidine on superoxide dismutase activity, H2O2 and superoxide radical level in barley leaves under water deficit conditions. Acta Physiol Plant 27:289–295. https://doi.org/10.1007/s11738-005-0005-7
Kuldau G, Bacon C (2008) Clavicipitaceous endophytes: their ability to enhance resistance of grasses to multiple stresses. Biol Control 46:57–71. https://doi.org/10.1016/j.biocontrol.2008.01.023
Kusano T, Berberich T, Tateda C, Takahashi Y (2008) Polyamines: essential factors for growth and survival. Planta 228:367–381. https://doi.org/10.1007/s00425-008-0772-7
Kuznetsov VV, Shevyakova NI (2007) Polyamines and stress tolerance of plants. Plant Stress 1:50–71
Kytöviita MM, Sarjala T (1997) Effects of defoliation and symbiosis on polyamine levels in pine and birch. Mycorrhiza 7:107–111. https://doi.org/10.1007/s005720050170
Leuchtmann A, Bacon CW, Schardl CL, Jr WJ, Tadych M (2014) Nomenclatural realignment of Neotyphodium species with genus Epichloë. Mycologia 106:202–215. https://doi.org/10.3852/106.2.202
Ma M, Christensen MJ, Nan Z (2015) Effects of the endophyte Epichloë festucae var. lolii of perennial ryegrass ( Lolium perenne ) on indicators of oxidative stress from pathogenic fungi during seed germination and seedling growth. Eur J Plant Pathol 141:571–583. https://doi.org/10.1007/s10658-014-0563-x
Malinowski DP, Belesky DP (2000) Adaptations of endophyte-infected cool-season grasses to environmental stresses: mechanisms of drought and mineral stress tolerance. Crop Sci 40:923–940. https://doi.org/10.2135/cropsci2000.404923x
Margosiak SA, Dharma A, Brucecarver MR, Gonzales AP, Louie D, Kuehn GD (1990) Identification of the large subunit of ribulose 1,5-bisphosphate carboxylase/oxygenase as a substrate for transglutaminase in Medicago sativa L. (alfalfa). Plant Physiol 92:88–96. https://doi.org/10.1104/pp.92.1.88
Martin-Tanguy J (1997) Conjugated polyamines and reproductive development: biochemical, molecular and physiological approaches. Physiol Plant 100:675–688. https://doi.org/10.1111/j.1399-3054.1997.tb03074.x
Miller G, Shulaev V, Mittler R (2008) Reactive oxygen signaling and abiotic stress. Physiol Plant 133:481–489. https://doi.org/10.1111/j.1399-3054.2008.01090.x
Monnet F, Vaillant N, Hitmi A, Coudret A, Sallanon H (2001) Endophytic Neotyphodium lolii induced tolerance to Zn stress in Lolium perenne. Physiol Plant 113:557–563. https://doi.org/10.1034/j.1399-3054.2001.1130415.x
Moon CD, Miles CO, Järlfors U, Schardl CL (2002) The evolutionary origins of three new Neotyphodium endophyte species from grasses indigenous to the southern hemisphere. Mycologia 94:694–711. https://doi.org/10.2307/3761720
Mutlu F, Bozcuk S (2005) Effects of salinity on the contents of polyamines and some other compounds in sunflower plants differing in salt tolerance. Russ J Plant Physiol 52:29–34. https://doi.org/10.1007/s11183-005-0005-x
Negrel J, Lherminier J (1987) Peroxidase-mediated integration of tyramine into xylem cell walls of tobacco leaves. Planta 172:494–501. https://doi.org/10.1007/BF00393865
Oberhofer M, Güsewell S, Leuchtmann A (2014) Effects of natural hybrid and non-hybrid Epichloë endophytes on the response of Hordelymus europaeus to drought stress. New Phytol 201:242–253. https://doi.org/10.1111/nph.12496
Omar MNA, Osman MEH, Kasim WA, El-Daim IAA (2009) Improvement of salt tolerance mechanisms of barley cultivated under salt stress using Azospirillum brasilense. In: Ashraf M, Ozturk M, Athar HR (eds) Salinity and water stress: improving crop efficiency. Springer, Dordrecht, pp 133–147
Pál M, Kovács V, Vida G, Szalai G, Janda T (2011) Changes in salicylic acid and polyamine contents following powdery mildew infection of near-isogenic thatcher-based wheat lines carrying different Lr genes. Acta Biol Szeged 55:139–141
Pál M, Szalai G, Janda T (2015) Speculation: polyamines are important in abiotic stress signaling. Plant Sci 237:16–23. https://doi.org/10.1016/j.plantsci.2015.05.003
Parádi I, Bratek Z, Láng F (2003) Influence of arbuscular mycorrhiza and phosphorus supply on polyamine content, growth and photosynthesis of Plantago lanceolata. Biol Plant 46:563–569. https://doi.org/10.1023/A:1024819729317
Pottosin I, Shabala S (2014) Polyamines control of cation transport across plant membranes: implications for ion homeostasis and abiotic stress signaling. Front Plant Sci 5:154. https://doi.org/10.3389/fpls.2014.00154
Prakash L, Prathapasenan G (1988) Effect of NaCl salinity and putrescine on shoot growth, tissue ion concentration and yield of rice (Oryza sativa L. var. GR-3). J Agron Crop Sci 160:325–334. https://doi.org/10.1111/j.1439-037X.1988.tb00630.x
Reza SM, Mirlohi A (2010) Neotyphodium endophytes trigger salt resistance in tall and meadow fescues. J Plant Nutr Soil Sci 173:952–957. https://doi.org/10.1002/jpln.200900345
Rodriguez RJ, Henson J, Volkenburgh EV, Hoy M, Wright L, Beckwith F, Kim YO, Redman RS (2008) Stress tolerance in plants via habitat-adapted symbiosis. ISME J 2:404–416. https://doi.org/10.1038/ismej.2007.106
Roy SJ, Negrão S, Tester M (2014) Salt resistant crop plants. Curr Opin Biotechnol 26:115–124. https://doi.org/10.1016/j.copbio.2013.12.004
Roychoudhury A, Basu S, Sengupta DN (2011) Amelioration of salinity stress by exogenously applied spermidine or spermine in three varieties of indica rice differing in their level of salt tolerance. J Plant Physiol 168:317–328. https://doi.org/10.1016/j.jplph.2010.07.009
Rozpądek P, Rozpadek P, Wezowicz K, Nosek M, Wazny R, Tokarz K, Lembicz M, Miszalski Z, Turnau K (2015) The fungal endophyte Epichloë typhina improves photosynthesis efficiency of its host orchard grass (Dactylis glomerata). Planta 242:1025–1035. https://doi.org/10.1007/s00425-015-2337-x
Saha J, Brauer EK, Sengupta A, Popescu SC, Gupta K, Gupta B (2015) Polyamines as redox homeostasis regulators during salt stress in plants. Front Environ Sci 3:21. https://doi.org/10.3389/fenvs.2015.00021
Saikkonen K, Wäli P, Helander M, Faeth SH (2004) Evolution of endophyte-plant symbioses. Trends Plant Sci 9:275–280. https://doi.org/10.1016/j.tplants.2004.04.005
Saikkonen K, Lehtonen P, Helander M, Koricheva J, Faeth SH (2006) Model systems in ecology: dissecting the endophyte-grass literature. Trends Plant Sci 11:428–433. https://doi.org/10.1016/j.tplants.2006.07.001
Saikkonen K, Gundel PE, Helander M (2013) Chemical ecology mediated by fungal endophytes in grasses. J Chem Ecol 39:962–968. https://doi.org/10.1007/s10886-013-0310-3
Sannazzaro AI, Echeverría M, Albertó EO, Ruiz OA, Menéndez AB (2007) Modulation of polyamine balance in Lotus glaber by salinity and arbuscular mycorrhiza. Plant Physiol Biochem 45:39–46. https://doi.org/10.1016/j.plaphy.2006.12.008
Santa-Cruz A, Acosta M, Pérez-Alfocea F, Bolarin MC (1997) Changes in free polyamine levels induced by salt stress in leaves of cultivated and wild tomato species. Physiol Plant 101:341–346. https://doi.org/10.1111/j.1399-3054.1997.tb01006.x
Schardl CL, Young CA, Hesse U, Amyotte SG, Andreeva K, Calie PJ, Fleetwood DJ, Haws DC, Moore N, Oeser B, Panaccione DG, Schweri KK, Voisey CR, Farman ML, Jaromczyk JW, Roe BA, O'Sullivan DM, Scott B, Tudzynski P, An Z, Arnaoudova EG, Bullock CT, Charlton ND, Chen L, Cox M, Dinkins RD, Florea S, Glenn AE, Gordon A, Güldener U, Harris DR, Hollin W, Jaromczyk J, Johnson RD, Khan AK, Leistner E, Leuchtmann A, Li C, Liu JG, Liu J, Liu M, Mace W, Machado C, Nagabhyru P, Pan J, Schmid J, Sugawara K, Steiner U, Takach JE, Tanaka E, Webb JS, Wilson EV, Wiseman JL, Yoshida R, Zeng Z (2013) Plant-symbiotic fungi as chemical engineers: multi-genome analysis of the Clavicipitaceae reveals dynamics of alkaloid loci. PLoS Genet 9:e1003323. https://doi.org/10.1371/journal.pgen.1003323
Shabala S, Demidchik V, Shabala L, Cuin TA, Smith SJ, Miller AJ, Davies JM, Newman IA (2006) Extracellular Ca2+ ameliorates NaCl-induced K+ loss from arabidopsis root and leaf cells by controlling plasma membrane K+-permeable channels. Plant Physiol 141:1653–1665. https://doi.org/10.1104/pp.106.082388
Shabala S, Cuin TA, Pottosin I (2007) Polyamines prevent NaCl-induced K+ efflux from pea mesophyll by blocking non-selective cation channels. FEBS Lett 581:1993–1999. https://doi.org/10.1016/j.febslet.2007.04.032
Smith G, Cloutt BA, Lynch DE, Byriel KA, Kennard CHL (1998) Influence of arbuscular mycorrhizae and rhizobium on free polyamines and proline levels in water-stressed alfalfa. J Plant Physiol 153:706–711. https://doi.org/10.1016/S0176-1617(98)80224-1
Song ML (2015) Mechanisms of salt tolerance improved by Epichloë endophyte in wild barley. Dissertation: Lanzhou University
Song ML, Chai Q, Li XZ, Yao X, Li CJ, Christensen MJ, Nan ZB (2015a) An asexual Epichloë endophyte modifies the nutrient stoichiometry of wild barley (Hordeum brevisubulatum) under salt stress. Plant Soil 387:153–165. https://doi.org/10.1007/s11104-014-2289-0
Song ML, Li XZ, Saikkonen K, Li CJ, Nan ZB (2015b) An asexual Epichloë endophyte enhances waterlogging tolerance of Hordeum brevisubulatum. Fungal Ecol 13:44–52. https://doi.org/10.1016/j.funeco.2014.07.004
Soto-Barajas MC, Zabalgogeazcoa I, Gómez-Fuertes J, González-Blanco V, Vázquez-De-Aldana BR (2016) Epichloë endophytes affect the nutrient and fiber content of Lolium perenne regardless of plant genotype. Plant Soil 405:265–277. https://doi.org/10.1007/s11104-015-2617-z
Tanaka A, Christensen M, Takemoto D, Park P, Scott B (2006) Reactive oxygen species play a role in regulating a fungus-perennial ryegrass mutualistic interaction. Plant Cell 18:1052–1066. https://doi.org/10.1105/tpc.105.039263
Tiburcio AF, Altabella T, Bitrián M, Alcázar R (2014) The roles of polyamines during the lifespan of plants: from development to stress. Planta 240:1–18. https://doi.org/10.1007/s00425-014-2055-9
Tytti S, Seppo K (2002) Potassium nutrition and free polyamines of Betula pendula Roth and Betula pubescens Ehrh. Plant Soil 238:141–149. https://doi.org/10.1023/A:1014262213688
Waie B, Rajam MV (2003) Effect of increased polyamine biosynthesis on stress responses in transgenic tobacco by introduction of human S-adenosylmethionine gene. Plant Sci 164:727–734. https://doi.org/10.1016/S0168-9452(03)00030-X
Walters DR (2000) Polyamines in plant-microbe interactions. Physiol Mol Plant Pathol 57:137–146. https://doi.org/10.1006/pmpp.2000.0286
Walters DR (2003) Polyamines and plant disease. Phytochemistry 64:97–107. https://doi.org/10.1016/S0031-9422(03)00329-7
Walters DR, Wylie MA (1986) Polyamines in discrete regions of barley leaves infected with the powdery mildew fungus, Erysiphe graminis. Physiol Plant 67:630–633. https://doi.org/10.1111/j.1399-3054.1986.tb05068.x
Wang CM, Xia ZR, Wu GQ, Yuan HJ, Wang XR, Li JH, Tian FP, Zhang Q, Zhu XQ, He JJ, Kumar T, Wang XL, Zhang JL (2016) The coordinated regulation of Na+ and K+ in Hordeum brevisubulatum responding to time of salt stress. Plant Sci 252:358–366. https://doi.org/10.1016/j.plantsci.2016.08.009
White JF Jr, Torres MS (2010) Is plant endophyte-mediated defensive mutualism the result of oxidative stress protection? Physiol Plant 138:440–446. https://doi.org/10.1111/j.1399-3054.2009.01332.x
Wimalasekera R, Tebartz F, Scherer GF (2011) Polyamines, polyamine oxidases and nitric oxide in development, abiotic and biotic stresses. Plant Sci 181:593–603. https://doi.org/10.1016/j.plantsci.2011.04.002
Xia C, Zhang XX, Christensen MJ, Nan ZB, Li CJ (2015) Epichloë endophyte affects the ability of powdery mildew (Blumeria graminis) to colonise drunken horse grass (Achnatherum inebrians). Fungal Ecol 16:26–33. https://doi.org/10.1016/j.funeco.2015.02.003
Xia C, Li NN, Zhang XX, Feng Y, Christensen MJ, Nan ZB (2016) An Epichloë endophyte improves photosynthetic ability and dry matter production of its host Achnatherum inebrians infected by Blumeria graminis under various soil water conditions. Fungal Ecol 22:26–34. https://doi.org/10.1016/j.funeco.2016.04.002
Yamaguchi Y, Sano H (2003) Induction of hypersensitive cell death by hydrogen peroxide produced through polyamine degradation in tobacco plants. Plant Physiol 132:1973–1981. https://doi.org/10.1104/pp.103.024737
Yamasaki H, Cohen MF (2006) NO signal at the crossroads: polyamine-induced nitric oxide synthesis in plants? Trends Plant Sci 11:522–524. https://doi.org/10.1016/j.tplants.2006.09.009
Zapata PJ, Serrano M, Pretel MT, Amoros A, Botella MA (2004) Polyamines and ethylene changes during germination of different plant species under salinity. Plant Sci 167:781–788. https://doi.org/10.1016/j.plantsci.2004.05.014
Zepeda-Jazo I, Shabala S, Chen Z, Pottosin II (2008) Na+-K+ transport in roots under salt stress. Plant Signal Behav 3:401–403. https://doi.org/10.4161/psb.3.6.5429
Zepeda-Jazo I, Velarde-Buendia AM, Enriquez-Figueroa R, Bose J, Shabala S, Muniz-Murguia J, Pottosin II (2011) Polyamines interact with hydroxyl radicals in activating Ca2+ and K+ transport across the root epidermal plasma membranes. Plant Physiol 157:2167–2180. https://doi.org/10.1104/pp.111.179671
Zhang XX, Li CJ, Nan ZB (2010) Effects of cadmium stress on growth and anti-oxidative systems in Achnatherum inebrians symbiotic with Neotyphodium gansuense. J Hazard Mater 175:703–709. https://doi.org/10.1016/j.jhazmat.2009.10.066
Zhao F, Song CP, He J, Zhu H (2007) Polyamines improve K+/Na+ homeostasis in barley seedlings by regulating root ion channel activities. Plant Physiol 145:1061–1072. https://doi.org/10.1104/pp.107.105882
Funding
The study was supported by National Basic Research Program of China (2014CB138702), the Natural Science Foundation of China (31372366), the Strategic Priority Research Program of Chinese Academy of Sciences (XDAXDA20100102), Program for Changjiang Scholars and Innovative Research Team in University of China (IRT17R50), Fundamental Research Funds for the Central Universities (LZUJBKY-2018-kb10), 111Project (B12002), USDA-NIFA Multistate Project W3147 and the New Jersey Agricultural Experiment Station.
Author information
Authors and Affiliations
Corresponding author
Ethics declarations
Conflict of interest
The authors declare that they have no conflicts of interest.
Disclosures
The article does not contain any studies with human participants or animals performed by any of the authors.
Informed consent
This study did not involve human participants, and so informed consent was not required.
Additional information
Responsible Editor: Birgit Mitter.
Rights and permissions
About this article
Cite this article
Chen, T., Li, C., White, J.F. et al. Effect of the fungal endophyte Epichloë bromicola on polyamines in wild barley (Hordeum brevisubulatum) under salt stress. Plant Soil 436, 29–48 (2019). https://doi.org/10.1007/s11104-018-03913-x
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s11104-018-03913-x