Skip to main content

Mycorrhizal symbiosis promotes the nutrient content accumulation and affects the root exudates in maize

Abstract

Background

Arbuscular mycorrhizal fungi (AMF) are a group of important symbiotic microorganisms found in ecosystems. Maize is the second most produced food crop globally. To investigate the mechanisms by which mycorrhizal symbiosis improves maize yields, the effects of mycorrhizal symbiosis on root vigor, nutrient accumulation in various tissues, and root exudates were investigated. We propose the following hypothesis: The secretion of organic acids in root exudates has antagonistic or synergistic effects, which are related to the rhizosphere environment. AMF symbiosis will enhance this effect.

Result

Rhizophagus aggreatus, Claroideoglomus etunicatum, and Funneliformis mosseae were used to inoculate maize plants separately; meanwhile, maize was inoculated with the above three fungi together for another processing. The plant tissues were sampled at five growth stages: V12 (twelve-leaf), VT (Tassel), R1 (Silking), R2 (Blister), and R4 (Dough stage). The root vigor, and nutrient content in different maize organs and organic acids in root exudates were determined in these stages. The results show that mycorrhizal symbiosis significantly improved the root vigor of maize, especially for plants inoculated with F. mosseae. AMF symbiosis significantly increased N, P, and K accumulation. Mixed inoculation with arbuscular mycorrhizal fungi significantly promoted the accumulation of N and K in maize. P accumulation was significantly promoted by C. etunicatum inoculation. Mycorrhizal symbiosis reduced the levels of protocatechuic, vanillic, citric, and ferulic acid in maize root exudates and increased the levels of p-hydroxybenzoic and caffeic acid. Except for syringic, chlorogenic and succinic acid, the levels of other organic acids in root exudates were higher in plants inoculated with F. mosseae than in other treatments.

Conclusion

This study demonstrates that mycorrhizal symbiosis improves root vigor and promotes nutrient accumulation at various sites; in addition, mycorrhizal symbiosis affects the content of organic acids in root exudates.

Peer Review reports

Background

Arbuscular mycorrhizal fungi (AMF) are widely distributed in nature and can form symbionts with more than 80% of plant roots in terrestrial ecosystems [1, 2]. As an important part of the natural ecosystem, they have a great impact on plant growth and production [3]. AMF symbiosis can promote the growth of host plants, increase yields and promote nutrient uptake by host plants [4]. In cases of insufficient nutrient supply, AMF symbiosis can significantly promote host plant absorption and nutrient utilization [5]. Furthermore, AMF ensure the normal growth of plants, improve plant productivity and affect dry matter distribution [6]. Their role is more obvious under conditions of P deficiency [7]. Research has found that multiple AMF combined with colonization play a greater role in promoting host growth [8]. For example, mixed inoculation with AMF could significantly improve the nutrient uptake efficiency and biomass of host plants and significantly improve the ability of host plants to combat salt stress. Previous research has shown that AMF symbiosis can affect root exudates of host plants, improving the stress resistance and nutrient absorption capacity of host plants [9, 10].

The role of root exudates in plant growth has attracted more attention from researchers [11]. Root exudates can improve soil enzymes, and microbial activities, accelerate the decomposition of plant litter [12], and affect the absorption and utilization of nutrients by plants [13, 14]. Some studies have found that plants release more root exudates under insufficient nutrient supply to promote the absorption and utilization of nutrients [15]; plant root exudates are affected by many factors, including biological and environmental factors [16]. Previous studies have investigated whether a high aluminum content can induce plants to secrete more citric acid [17,18,19], which may be related to the effect of root exudates on soil properties, organic pollutant migration and activity [20,21,22]. These studies show that AMF symbiosis could affect the root exudates of Artemisia annua and thus enhance the allelopathy of Artemisia annua. Similarly, arbuscular mycorrhizal fungi can reduce the invasion of root-knot nematodes by changing the root exudates of their hosts [23].

Moreover, AMF symbiosis can improve insect resistance by affecting the root exudates of plants [24] and could also affect changes in phenolic acid levels in root exudates of cotton, thus improving cotton resistance to Fusarium wilt [25]. In other cases, it has been shown that AMF symbiosis could affect the root exudates of tomatoes, thus affecting the rhizosphere microbial community and improving the disease resistance of tomatoes [26].

Maize is the second most produced food crop globally and has become an economically important crop [27, 28]. AMF can induce changes in maize roots [29] and promote the absorption of nutrients in maize [30]. Studies have shown that AMF symbiosis can promote the accumulation of soluble sugar in maize roots and improve the tolerance of maize plants to salt and copper stress [31, 32]. AMF can also reduce the membrane lipid peroxidation and membrane permeability of maize, increase the accumulation of osmotic adjustment substances and antioxidant enzyme activities, reduce temperature stress damage to maize plants, improve the high-temperature tolerance of maize plants, and promote their growth [33]. AMF symbiosis can also increase the number of microorganisms and soil microbial enzymes in the maize rhizosphere [34], improving maize resistance to sheath blight [35]. It was also found that the organic acids secreted by maize roots can alleviate paraquat damage to maize [36]. Nevertheless, the effect of AMF symbiosis on root exudates of maize is rarely reported. This research aimed to investigate the effect of AMF symbiosis on the changes in maize root vigor, nutrient content and distribution, and to explore the effects of organic acids content in maize root exudates after AMF symbiosis.

Materials and methods

Experimental materials

A greenhouse experiment was conducted at the College of Agriculture of Guangxi University in Nanning (22°50′N, 108°17′E), China, during 2018. The maize variety Zhengda 619 (the kernel type of this kind of maize is flint corn, a common single cross hybrid that can effectively resist leaf blight, Bipolaris maydis and sheath blight) was provided by the Zhengda seed industry in Sichuan, China. Three AMFs (isolated from the soil around the roots of maize plants on farmland and obtained after 1 year of maize propagation with Zhengda 619) were used in this experiment: Rhizophagus aggreatus, with a spore density of 78 num g− 1; Claroideoglomus etunicatum with a spore density of 71 num g− 1; and Funneliformis mosseae with a spore density of 75 nm g− 1. The experimental container was a plastic flower pot with a 35 cm × 25 cm height and diameter. Sterilized river sand (the sand was washed with water three times to remove impurities and then sterilized by the damp heat method for 24 h.) was used as a substrate to grow the maize plants.

Experimental design and methods

The maize seeds were washed three times with sterile water to remove impurities on the surface, soaked in 10% hydrogen peroxide for 1 min to remove miscellaneous bacteria on the surface of the seeds, and then washed with sterile water. The sterilized seeds were sown on filter paper in petri dishes under control conditions at 28 °C. The evenly germinated seeds were planted in pots filled with 4 kg sterilized river sand. Five treatments were designed: maize plants inoculated with Rhizophagus aggreratus were recorded as RA, those inoculated with Claroideoglomus etunicatum were recorded as CE, those inoculated with Funneliformis mosseae were recorded as FM, those inoculated with three species of AMF were recorded as MI, and those without AMF were recorded as CK. To set each treatment, 300 g of inoculant containing spores of Rhizophagus aggreratus, Claroideoglomus etunicatum and Funneliformis mosseae were added to RA, CE and FM, respectively; the above three kinds of inoculants each included 100 g for MI; sterilized sand without AMF was used as the CK treatment. In this experiment, a total of 150 pots were used. Each pot was filled with 6 maize seeds that germinated. When the corn plants grew two real leaves, thinning was carried out, and one plant was retained in each pot. The filtrates were collected by mixing 300 g each of the bacterial and sterilized sand together, rinsing with 5 L of sterile water, and then filtering through a 600-mesh strainer. The collected filtrates were evenly added to each pot, and 30 ml was added to each pot to ensure that the various pots had consistent microbial communities except with a difference in AMF. Each pot was irrigated with 300 ml of tap water once a week. Hogland’s nutrient solution was applied every 2 weeks from the emergence of corn plants to the 47th day and applied once a week from the 48th day to the 82nd day after emergence, applying 200 ml each time (the formula and concentration of nutrient solution are shown in the supplementary materials section).

The samples were collected during the twelve-leaf (V12, 47 days after planting), tasseling (VT, 67 days after planting), silking (R1, 74 days after planting), blister (R2, 82 days after planting), and dough (R4, 104 days after planting) stages. The plants were carefully uprooted, roots were thoroughly washed three times with distilled water to remove impurities and dried with filter paper, and samples were collected. The maize root tips were cut off to measure root vigor, and the remaining root parts were stored in 50% ethanol to determine the colonization rate of different AMF on the maize. For each treatment, another three corn plants were taken back to the laboratory, and the impurities on the roots were washed with distilled water to collect root exudates and detect the nutrient content of organs.

Determination of mycorrhizal colonization rate

The preserved plant root was subjected to transparency, decolorization, acidification, dyeing and fading treatment. For each treatment, 20 root segments were cut and placed on slides. The morphological structure, invasion point and vesicle of mycorrhizae were observed under a light microscope (LEICA DM300, Leica Microsystems Cms GmbH, Wetzlar, Germany). The colonization rate of mycorrhizae was slightly optimized following Liu [37]. The colonization rate was determined according to the following formula:

$$\mathrm{Mycorrhizal}\ \mathrm{colonization}\ \mathrm{rate}\ \left(\%\right)=\frac{\sum \mathrm{colonization}\kern0.17em \mathrm{rate}\;1+\mathrm{colonization}\kern0.17em \mathrm{rate}\;2\dots \dots +\mathrm{colonization}\kern0.17em \mathrm{rate}\;\mathrm{n}}{\mathrm{The}\kern0.17em \mathrm{total}\kern0.17em \mathrm{number}\kern0.17em \mathrm{of}\kern0.17em \mathrm{root}\kern0.17em \mathrm{segments}\kern0.17em \mathrm{observed}}\times 100$$

Determination of root vigor

The determination of root vigor was based on Liu’s method [38] with slight modifications. For instance, to draw a standard curve, dilutions of standard colorimetric solutions of 160 μl, 120 μl, 80 μl, 40 μl, and 20 μl were prepared and configured with 2, 3, 5-triphenyte-trazolium chloride (TTC), and the absorbance value was determined at 485 nm wavelength with methanol used as a control. Later, 0.5 g of root tip-sample was accurately weighed and transferred to a 100 ml calibration tube. A mixture of 0.4% TTC phosphoric acid buffer (1:1) was added. After 2 h of shading at 37 °C, the sample was shaken. The absorbance was measured at a wavelength of 485 nm, and the reduced amount of TTC (μg) was calculated. Root vigor was calculated as follows:

$$\mathrm{Reduction}\ \mathrm{strength}\ \mathrm{of}\ \mathrm{tetrazole}\ \left(\upmu \mathrm{g}\;{\mathrm{g}}^{-1}\;{\mathrm{h}}^{-1}\right)=\frac{\mathrm{Reduction}\kern0.17em \mathrm{of}\kern0.17em \mathrm{tetrazolium}\left(\upmu \mathrm{g}\right)}{\mathrm{Weight}\kern0.17em \mathrm{of}\kern0.17em \mathrm{root}\left(\mathrm{g}\right)\times \mathrm{Time}\left(\mathrm{h}\right)}$$

Determination of nutrient content

The roots, stems, leaves and grains of maize at harvest were dried to a constant weight and crushed. Approximately 0.1 g of the crushed sample was placed in a digestion tube. Then, 5 ml of concentrated sulfuric acid and 2 ml of H2O2 were added and left for 24 h. The above samples were placed on a boiler for digestion until colorless and transparent, collected and then cooled at room temperature. The sample was then transferred to a 50 ml volumetric flask, serving as the determination solution. Nutrient content in different plant tissues was determined [39]. Briefly, the total nitrogen level was determined by an AutoAnalyzer 3 continuous Flow Chemical Analyzer (Bran Luebbe, Norderstedt, Germany); phosphorus was measured by a spectrophotometer (Spectrum SP-1920, Shanghai, China), and potassium was determined by a flame photometer (Aopu AP1200, Shanghai, China).

Collection and detection of root exudates

The extraction and identification of root exudates were optimized on the basis of Badri’s method [16]. The root exudate concentrate was dissolved in chromatographic grade methanol (Fisher Scientific), passed through an organic filter membrane with a pore size of 0.22 μm (micropore), transferred to an injection bottle and stored at a low temperature.

An ultra-high-performance liquid chromatography (UPLC - QTOF; Waters Xevo G2-XS QTOF, Massachusetts, USA) chromatographic system was used to analyze the root exudates. Root exudates were separated by gradient elution on an HSS T3 column (Waters Acquity 1.8 μm, Massachusetts, USA). The mass spectrometry system included a quadrupole time flight mass analyzer (QTOF), and detection mode tandem mass spectrometry (MS/MS) was used. The specific UPLC and MS/MS conditions of each organic acid are presented in the supplementary materials section.

The content of organic acids in maize root exudates was quantitatively analyzed by Target Lynx (Waters). First, each organic acid’s quantitative ion and retention time were obtained from the standard sample, and the corresponding standard curve was drawn. The sample parameters obtained by UPLC-QTOF were brought into the standard curve to calculate the organic acid level.

Source of reagents: Standard organic acids (p-hydroxybenzoic acid, protocatechuic acid, vanillic acid, syringic acid, citric acid, p-coumaric acid, chlorogenic acid, caffeic acid, succinic acid, and ferulic acid) were purchased from Shanghai Yuanye Biotechnology Co., Ltd. (Shanghai, China).

Statistical analysis

All of the data obtained in this experiment were calculated using Microsoft Excel 2016, and statistical analyses were carried out using SPSS (Version 19.0; IBM, Inc.) software package for Windows. Statistically significant differences among treatments were determined by one-way ANOVA and least significant difference (LSD) calculations at the 95% confidence level. Figures were mapped using the R program (https://www.r-project.org/) and SigmaPlot (Version 10.0, Systat, Inc).

Results

Mycorrhizal colonization rate of maize by AMF at different growth stages

The fungal colonization rate of AMF increased with the extension of the maize growth period, but the colonization rate of AMF tended to stabilize at R2 and R4 (Fig. 1). At V12, there was a significant difference between MI (46.33%) and RA (36.33%). At VT, the fungal colonization of FM on maize increased rapidly, reaching 59.50%, with an increase of 58% compared to that of V12, and the increase rate and fungal colonization were the highest recorded throughout the whole growth period. At R1, the fungal colonization of R. aggreratus on maize increased by 42%, representing the largest increase occurring in this period. However, in this period, the AMF with the highest colonization rate (74.17%) of maize roots was F. mosseae. Up to R4, the fungal colonization levels of each treatment from high to low were ranked as CE > FM > MI > RA with percent values of 84.17, 79.83, 75.17 and 74.33%, respectively.

Fig. 1
figure 1

a Shows the changes in mycorrhizal colonization rates. b Shows the growth rate of the mycorrhizal customization rate V12 stands for the twelve-leaf stage (47 days after planting), VT stands for the tasseling stage (67 days after planting), R1 stands for the silking stage (74 days after planting), R2 stands for the blister stage (82 days after planting), and R4 stands for the dough stage (104 days after planting). RA denotes maize inoculated with R. aggratus, CE denotes maize inoculated with C. etunicatum, FM denotes maize inoculated with F. mosseae, MI denotes maize inoculated with the above three kinds of AMF, and CK denotes maize without AMF inoculation. The same applies below

Root vigor of maize after symbiosis with different AMF

The root vigor of maize at different growth stages is shown in Fig. 2. In the early stages of maize growth, the root vigor of RA, CE, and FM was significantly higher than that of CK, and that of CE was the highest. The root vigor of each treatment increased rapidly and reached the maximum value at VT, and in this growth period, the root vigor levels under the RA, CE, FM, MI and CK treatments were 359.64, 442.08, 451.44, 377.28, and 317.88 μg g− 1 h− 1, respectively. At R1, the root vigor of maize decreased and maintained a relatively stable state in the later growth period; however, the root vigor of maize symbiosis with AMF was always significantly higher than that of non-AMF symbiosis. After that start of R1, the root vigor of CE was always higher than that of the other treatments and significantly higher than that of CK.

Fig. 2
figure 2

Changes in root vigor of maize under different treatments at different growth stages. Lowercase letters in the figures indicate significant differences between treatments (p<0.05), and for treatment and plant growth details, see the legend of Fig. 1

Nutrient content of maize at different growth stages after symbiosis with different AMF

The total N, P and K levels of the maize plants were measured and analyzed during the harvest period. The results show that the accumulation of N, P and K in MI was the highest, and the accumulation capacity of N, P and K in maize symbiosis with AMF was significantly higher than that in CK (Fig. 3). AMF increased the accumulation of nutrients and affected the distribution of nutrients in maize organs relative to the control plants (Table 1). However, the AMF and combined treatments showed various effects on the accumulation of nutrients in the different growth stages. The effect of mycorrhizal and maize symbiosis on nutrient content was more obvious in the early and late stages than in the middle stage. For example, at V12, shortly after AMF and maize established a symbiotic relationship, the RA treatment helped maize leaves accumulate 31% more P than the CK treatment. The CE treatment accelerated the accumulation of N and K in leaves and of P and K in roots relative to the other treatments, and P accumulation in roots was 102% higher than that observed in CK. Similarly, higher N levels in roots and higher N and P levels in stems accumulated under the FM treatment in the V12 growth stage. In this regard, relative to the control, the N content in roots and P content in stems in the FM treatment increased by 114 and 157%, respectively. The nutrient contents of N, P and K in mycorrhizal symbiotic maize were significantly higher than those in AMF free maize at VT, R1 and R2. At the R4 growth stage, the dry matter accumulation of maize organs tended to be stable. After analyzing the data of this growth period, we found that the RA treatment promoted the accumulation of higher N and P in roots and more N in stems than the remaining treatment. For instance, the accumulation of N in stems was 78% higher than that in CK. Similarly, significantly higher P and K levels were found under the CE treatment in stems and roots, respectively. The accumulation of P in stems was 80% higher than that in CK. Treatment FM encouraged leaves to accumulate more N, and N accumulation was 22% higher than that under CK. The leaves of MI accumulated more P and K, and the stems accumulated more P. The accumulation of P in stems was 105% higher than that in CK. The accumulation of N, P and K in MI grains was also the highest, and P accumulation in MI grains was 109% higher than that in CK.

Fig. 3
figure 3

Nutrient content of maize in the harvest period. a Total nitrogen content of each treatment (g plant− 1), b phosphorus content in each treatment (g plant− 1), and c potassium content in each treatment (g plant− 1)

Table 1 Nutrient content in different tissues of maize under different treatments at different growth stages

Changes in organic acids in maize root exudates at different growth stages after symbiosis with AMF

The primary chromatograms of 10 organic acids standards are shown in Fig. 4. Different AMF inoculations had different effects on maize root exudates at different growth stages (Fig. 5). In this experiment, 10 kinds of organic acids were isolated from maize root exudates. At the V12 growth stage, syringic acid under treatment CE was 304.82% higher than that of CK, and succinic acid under treatment MI was 85.23% lower than that of CK. At the VT stage, the p-hydroxybenzoic acid levels were 166.40% higher under the RA treatment than under the CK treatment, but the secretion of ferulic acid was inhibited by C. etunicatum, and the ferulic acid level was 88.38% lower under the CE treatment than under the CK treatment. Similarly, in the R1 stage, the ferulic acid level was 68.96% lower upon the imposition of FM than without AMF treatment, and caffeic acid levels under CE treatment were 41.27% lower than those of CK. However, across the whole growth period, the total amount of caffeic acid in FM was significantly higher than that in all other treatments, including CK. The succinic acid content of treatment MI was 68.95% lower than that of CK at the R1 stage. At the R2 stage, FM had 168.81% more p-hydroxybenzoic acid than the CK treatment. The FM treatment promoted the secretion of p-hydroxybenzoic and p-coumaric acid at the R4 growth stage, with levels 41.71% higher than those of CK, and the succinic acid of MI was 66.07% lower than that of CK. Interestingly, regardless of the growth period, the succinic acid content of MI was the lowest across all treatments.

Fig. 4
figure 4

Primary chromatograms of 10 organic acids standards

Fig. 5
figure 5

Organic acids in maize root exudates under different AMF symbiosis levels (ppb). (a ~ j) show the differences in p-hydroxybenzoic acid, protocatechuic acid, vanillic acid, syringic acid, citric acid, p-coumaric acid, chlorogenic acid, caffeic acid, succinic acid, and ferulic acid secretion in different growth stages under different treatments. Different colored blocks in each stacked histogram represent different growth maize periods: orange blocks refer to R4 (dough stage), green blocks refer to R2 (blister), purple blocks refer to R1 (silking), yellow blocks refer to VT (tassel), and blue blocks refer to V12 (twelve leaf). Analysis of differences between groups was performed for different treatments of the same growth phase shown in each stained histogram with identical lowercase letters denoting no significant differences between treatments (P > 0.05) and with different lowercase letters denoting significant differences between treatments (P < 0.05). Lower case letters in figures differently indicate significant differences between treatments (p<0.05)

Correlation analysis of root exudates and nutrient allocation

To obtain an overall understanding of the effects of AMF symbiosis on maize root vigor, nutrient accumulation and organic acids in root exudates, we drew a cluster correlation heatmap for the obtained data, and the results are shown in Fig. 6. The results show that AMF symbiosis could improve the root vigor of maize, inhibit the levels of protocatechuic and ferulic acid in root exudates, increase levels of p-hydroxybenzoic and caffeic acid, and promote nutrient accumulation in various organs. The correlation coefficients between total nitrogen and total phosphorus content and mycorrhizal infection rates were the largest at 0.54. Root vigor was positively correlated with maize nutrient accumulation and had the greatest effect on leaf potassium content, and its Pearson correlation coefficient reached 0.81. Among the organic acids, ferulic acid generated the largest Pearson correlation coefficient with the mycorrhizal infection rate, and its Pearson coefficient reached − 0.42, indicating that mycorrhizal symbiosis significantly reduces the content of ferulic acid. The clustering results show that the mycorrhizal infection rate and total nitrogen content of maize belonged to the same cluster and were positively correlated, and the Pearson correlation coefficient was 0.54. Some rules of the clustering results of organic acids apply. Citric and chlorogenic acid belong to the same cluster, and their correlation coefficient is 0.24; butyric and p-coumaric acid belong to the same cluster, and their correlation coefficient is 0.72; P-hydroxybenzoic and vanillic acid belong to the same cluster, and their correlation coefficient is 0.83; caffeic and ferulic acid belong to the same cluster, and their correlation coefficient is 0.31.

Fig. 6
figure 6

Correlation clustering heatmap of the correlation analysis. The Pearson coefficient is obtained by analyzing the correlation between each index. The obtained Pearson coefficient is made into a correlation heatmap. Red fields denote a positive correlation between the two. The darker the color is, the stronger the correlation is. Blue fields denote the opposite result

Discussion

AMF can affect the growth, development and reproduction of host plants by regulating the absorption and recycling of nutrients. AMF symbiosis significantly increased the nutrient content of maize roots, stems and leaves, showing that AMF symbiosis could promote the nutrient content of host plants, which is consistent with the results of Chaudhary Year [4]. In addition, this study found that AMF symbiosis affects nutrient allocation in maize organs. The results show that R. aggrratus accumulated more N in maize leaves during VT. C. etunicatum caused maize roots to accumulate more N in the VT period and caused stems to accumulate more N in the R2 period and more P in the R4 period. F. mosseae caused maize roots to accumulate more K in the R2 period, roots to accumulated more P in the VT period, leaves to accumulated more P in the R4 period, and stems and leaves to accumulated more K in the R4 and VT periods, respectively. In all treatments, the joint action of the three AMFs most significantly promoted the accumulation of N, P and K in maize grains. AMF symbiosis significantly promoted maize nutrient accumulation, which is consistent with the research results of Chaudhary [4].

The root vigor of maize was higher at VT than at other growth periods. In this period, root vigor levels from high to low were ranked as follows: FM > CE > Mi > RA > CK. The root vigor of maize was affected by several factors, such as nutrient stress levels and cultivation methods used [15, 38]. AMF symbiosis improves plant root vigor under salt stress [40]. This study found that AMF symbiosis can still affect the root vigor of maize even without salt stress, and the root vigor of maize with AMF symbiosis was significantly higher than that of maize without AMF symbiosis in each growth stage. In addition, different AMFs have different effects on maize root vigor.

Our current study only explored changes in some organic acids in corn root exudates after AMF symbiosis. From the total level of organic acids secretion in the whole maize growth period, we found that FM promoted the secretion of p-hydroxybenzoic, p-coumaric and caffeic acid. CE promoted the secretion of syringic acid, and RA promoted the secretion of chlorogenic and succinic acid. The levels of protocatechuic, vanillic, citric and ferulic acid were lower than those of CK. Some studies have shown that p-hydroxybenzoic acid can reduce the number of Fusarium and the occurrence of Fusarium wilt [41]; vanillic acid can inhibit soil-borne pathogens and reduce soil-borne diseases [42]. Vanillic acid can inhibit the growth of Fusarium wilt [43]; caffeic acid plays an important role in inhibiting soil-borne pathogens, and caffeic acid can directly inhibit the growth of Ralstonia solanacearum [44]. AMF may alleviate soil-borne diseases [45] by increasing the levels of p-hydroxybenzoic, vanillic and caffeic acid in plant root exudates. In addition, AMF symbiosis promotes the secretion of syringic acid and inhibits the secretion of ferulic acid. Syringic acid can change the microbial community in the rhizosphere and the structure of bacterial and fungal communities in the rhizosphere [46]. Ferulic acid has strong allelopathy and can inhibit the growth of plant roots [47]. It was found that a change in plant root exudates affects the activity of rhizosphere soil microorganisms and then the composition of the microbial community [48, 49], which may be related to the promotion of syringic acid secretion by AMF symbiosis. Moreover, AMF symbiosis alleviates the continuous cropping obstacle [50], which may be related to a decrease in ferulic acid secretion. The effect of AMF symbiosis on organic acids in root exudates may be an important means through which AMF improves host plant resistance, alleviates continuous cropping barriers and promotes nutrient uptake. In general, the secretion of organic acids varied with different maize growth stages. AMF symbiosis further affected the content of organic acids in maize root exudates, and this effect was related to the type of AMF involved and the maize growth period. However, the role of these organic acids in maize growth and their impact on maize growth after AMF symbiosis must be further studied and discussed, potentially through exogenous application. In subsequent experiments, we will also further study and verify the effects of these organic acids on maize. From Fig. 6, we found that after mycorrhizal symbiosis, maize root vigor and nutrient accumulation were promoted synchronously, showing that the improvement of maize root vigor after mycorrhizal symbiosis may be an important reason behind the improvement in nutrient accumulation. Therefore, it is speculated that after mycorrhizal symbiosis, mycorrhizal symbiosis promotes the capacity for nutrient uptake and then the accumulation of nutrients in maize by enhancing root viability. From our cluster analysis results, we conclude that the content of organic acids was closely related to leaf N content and that root vigor was closely related to root N and P levels and leaf K content, whereas the mycorrhizal infection rate and total N, P, and K levels of maize plants, leaf P content, stem N content, and root K content were related. Some rules govern organic acids content in root exudates of maize, as p-hydroxybenzoic, vanillic, ferulic, symbolic, p-coumaric, cash and succinic acid did not increase synchronously; there was also a negative correlation between p-hydroxybenzoic, protocatechuic and citric acid. We know that antagonistic or synergistic effects occur between endogenous plant hormones [51]. Based on previous studies and our results, we speculate that there should also be antagonism or synergy between organic acids in root exudates closely related to the plant rhizosphere environment.

Conclusion

Our results suggest that different mycorrhizal fungi play different roles after symbiosis with maize. R. aggreratus promotes the accumulation of N and P in maize roots and of N in stems. C. etunicatum encourages roots to accumulate more K and stems to accumulate more P. F. mosseae was found to have the greatest effect on the root vigor of maize and encouraged leaves to accumulate more N. The three AMF treatments promoted the accumulation of more K in stems and promoted the accumulation of more P and K in leaves, while promoting the accumulation of more N, P, and K in grains. Different mycorrhizae have different effects on root exudates. R. aggreratus had the greatest effect on maize root exudates at the VT growth stage, C. etunicatum had the greatest effect on maize root exudates at the V12 growth stage, and F. mosseae had the greatest effect on maize root exudates at the R1 and R2 growth stages.

We conclude that AMF symbiosis could significantly improve root vigor, promote the accumulation of nutrients, and affect nutrient distribution, and these changes are significantly correlated with changes in root exudates. The results of this study can preliminarily explain the relationship between root exudates after AMF symbiosis and provide a theoretical basis for the mechanism of improving maize yield after AMF symbiosis. The presented results also provide a theoretical basis for research on AMF use in microbial fertilizers.

Availability of data and materials

The datasets used and analysed during the current study available from the corresponding author on reasonable request.

Abbreviations

V12:

Twelve-leaf stage (47 days after planting)

VT:

Tasseling stage (67 days after planting)

R1:

Silking stage (74 days after planting)

R2:

Blister stage (82 days after planting)

R4:

Dough stage (104 days after planting).

RA:

Maize plants inoculated with Rhizophagus aggreratus

CE:

Maize plants inoculated with Claroideoglomus etunicatum

FM:

Maize plants inoculated with Funneliformis mosseae

MI:

Maize plants inoculated with Rhizophagus aggreratus, Claroideoglomus etunicatum and Funneliformis mosseae

CK:

Maize plants without AMF

References

  1. Johnson NC, Graham JH, Smith FA. Functioning of mycorrhizal associations along the mutualism-parasitism continuum. New Phytol. 1997;135:575–86.

    Article  Google Scholar 

  2. Koide RT, Mosse B. A history of research on arbuscular mycorrhiza. Mycorrhiza. 2004;14:145–63.

    Article  PubMed  Google Scholar 

  3. Kivlin SN, Hawkes CV, Treseder KK. Global diversity and distribution of arbuscular mycorrhizal fungi. Soil Biol Biochem. 2011;43:2294–303.

    Article  CAS  Google Scholar 

  4. Chaudhary V, Kapoor R, Bhatnagar AK. Effectiveness of two arbuscular mycorrhizal fungi on concentrations of essential oil and artemisinin in three accessions of Artemisia annua L. Appl Soil Ecol. 2008;40:174–81.

    Article  Google Scholar 

  5. Li H, Smith SE, Holloway RE, Zhu Y, Smith FA. Arbuscular mycorrhizal fungi contribute to phosphorus uptake by wheat grown in a phosphorus-fixing soil even in the absence of positive growth responses. New Phytol. 2006;172:536–43.

    Article  CAS  PubMed  Google Scholar 

  6. Sulman BN, Brzostek ER, Medici C, Shevliakova E, Menge DNL, Phillips RP. Feedbacks between plant N demand and rhizosphere priming depend on type of mycorrhizal association. Ecol Lett. 2017;20:1043–53.

    Article  PubMed  Google Scholar 

  7. Xu J, Liu S, Song S, Guo H, Tang J, Yong JWH, et al. Arbuscular mycorrhizal fungi influence decomposition and the associated soil microbial community under different soil phosphorus availability. Soil Biol Biochem. 2018;120:181–90.

    Article  CAS  Google Scholar 

  8. Heidarianpour MB, Aliasgharzad N, Olsson PA. Positive effects of co-inoculation with Rhizophagus irregularis and Serendipita indica on tomato growth under saline conditions, and their individual colonization estimated by signature lipids. Mycorrhiza. 2020;30:455–66.

    Article  CAS  PubMed  Google Scholar 

  9. Nagahashi G, Douds D. Separated components of root exudate and cytosol stimulate different morphologically identifiable types of branching responses by arbuscular mycorrhizal fungi. Mycol Res. 2007;111:487–92.

    Article  PubMed  Google Scholar 

  10. Fusconi A. Regulation of root morphogenesis in arbuscular mycorrhizae:what role do fungal exudates, phosphate, sugars and hormones play in lateral root formation? Ann Bot-London. 2014;113:19–33.

    Article  CAS  Google Scholar 

  11. Sun C, Wang D, Shen X, Li C, Liu J, Lan T, et al. Effects of biochar, compost and straw input on root exudation of maize (Zea mays L.): from function to morphology. Agric Ecosyst Environ. 2020;297:106952.

    Article  CAS  Google Scholar 

  12. Tian K, Kong X, Yuan L, Lin H, He Z, Yao B, et al. Priming effect of litter mineralization:the role of root exudate depends on its interactions with litter quality and soil condition. Plant Soil. 2019;440:457–71.

    Article  CAS  Google Scholar 

  13. Coskun D, Britto DT, Shi W, Kronzucker HJ. How plant root exudates shape the nitrogen cycle. Trends Plant Sci. 2017;22:661–73.

    Article  CAS  PubMed  Google Scholar 

  14. Ravazzolo L, Trevisan S, Manoli A, Boutet-Mercey SP, Perreau FO, Quaggiotti S. The control of Zealactone biosynthesis and exudation is involved in the response to nitrogen in maize root. Plant Cell Physiol. 2019;60:2100–12.

    Article  CAS  PubMed  Google Scholar 

  15. Gaume A, Mächler F, León CD, Narro L, Frossard E. Low-P tolerance by maize. Zea mays L genotypes: significance of root growth, and organic acids and acid phosphatase root exudation. Plant Soil. 2001;228:253–64.

    Article  CAS  Google Scholar 

  16. Badri DV, Loyola VM, Broeckling CD, Vivanco JM. Root secretion of phytochemicals in Arabidopsis is predominantly not influenced by diurnal rhythms. Mol Plant. 2010;3:491–8.

    Article  CAS  PubMed  Google Scholar 

  17. Chaffai R, Nouhou Seybou T, Marzouk B, Ferjani E. Changes induced by aluminum stress in the organic acid content of maize seedlings: the crucial role of exogenous citrate in enhancing seedling growth. Biologia. 2009;64(6):1129–35.

  18. Yang J, Fan W, Zheng S. Mechanisms and regulation of aluminum-induced secretion of organic acid anions from plant roots. J Zhejiang Univ-Sc B. 2019;20:513–27.

    Article  CAS  Google Scholar 

  19. Li W, Finnegan PM, Dai Q, Guo D, Yang M. Metabolic acclimation supports higher aluminium-induced secretion of citrate and malate in an aluminium-tolerant hybrid clone of Eucalyptus. BMC Plant Biol. 2021;21(1):14.

  20. Zhu Y, Zhang S, Huang H, Wen B. Effects of maize root exudates and organic acids on the desorption of phenanthrene from soils. J Environ Sci-China. 2009;21(7):920–6.

    Article  CAS  PubMed  Google Scholar 

  21. Rodríguez-Garrido B, Balseiro-Romero M, Kidd PS, Monterroso C. Effect of plant root exudates on the desorption of hexachlorocyclohexane isomers from contaminated soils. Chemosphere. 2020;241:124920.

    Article  PubMed  Google Scholar 

  22. Sun CY, Zeng YH, Ma JQ, Liu L, Liao HL, Huang JH. Effects of arbuscular mycorrhizal fungi inoculation on allelopathic potential of Artemisia annua L. root exudates. Allelopathy J. 2019;48:175–90.

    Article  Google Scholar 

  23. Vos C, Claerhout S, Mkandawire R, Panis B, De Waele D, Elsen A. Arbuscular mycorrhizal fungi reduce root-knot nematode penetration through altered root exudation of their host. Plant Soil. 2012;354:335–45.

    Article  CAS  Google Scholar 

  24. Louarn J, Carbonne F, Delavault P, Bécard G, Rochange S. Reduced germination of Orobanche cumana seeds in the presence of arbuscular mycorrhizal fungi or their exudates. PLoS One. 2012;7(11):e49273.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  25. Zhang G, Raza W, Wang X, Ran W, Shen Q. Systemic modification of cotton root exudates induced by arbuscular mycorrhizal fungi and Bacillus vallismortis HJ-5 and their effects on Verticillium wilt disease. Appl Soil Ecol. 2012;61:85–91.

    Article  CAS  Google Scholar 

  26. Lioussanne L, Perreault F, Jolicoeur M, St-Arnaud M. The bacterial community of tomato rhizosphere is modified by inoculation with arbuscular mycorrhizal fungi but unaffected by soil enrichment with mycorrhizal root exudates or inoculation with Phytophthora nicotianae. Soil Biol Biochem. 2010;42:473–83.

    Article  CAS  Google Scholar 

  27. Poole N, Donovan J, Erenstein O. Agri-nutrition research: revisiting the contribution of maize and wheat to human nutrition and health. Food Policy. 2020;100:101976.

  28. Tanumihardjo SA, McCulley L, Roh R, Lopez-Ridaura S, Palacios-Rojas N, Gunaratna NS. Maize agro-food systems to ensure food and nutrition security in reference to the sustainable development goals. Glob Food Security. 2020;25:100327.

    Article  Google Scholar 

  29. Chen XW, Wu L, Luo N, Mo CH, Wong MH, Li H. Arbuscular mycorrhizal fungi and the associated bacterial community influence the uptake of cadmium in rice. Geoderma. 2019;337:749–57.

    Article  CAS  Google Scholar 

  30. Barea JM, Bonis AF, Olivares J. Interactions between azospirillum and va mycorrhiza and their effects on growth and nutrition of maize and ryegrass. Soil Biol Biochem. 1983;15(6):705–9.

    Article  Google Scholar 

  31. Feng G, Zhang FS, Li XL, Tian CY, Tang C, Rengel Z. Improved tolerance of maize plants to salt stress by arbuscular mycorrhiza is related to higher accumulation of soluble sugars in roots. Mycorrhiza. 2002;12(4):185–90.

    Article  CAS  PubMed  Google Scholar 

  32. Merlos MA, Zitka O, Vojtech A, Azcón-Aguilar C, Ferrol N. The arbuscular mycorrhizal fungus Rhizophagus irregularis differentially regulates the copper response of two maize cultivars differing in copper tolerance. Plant Sci. 2016;253:68–76.

    Article  CAS  PubMed  Google Scholar 

  33. Zhu X, Song F, Xu H. Influence of arbuscular mycorrhiza on lipid peroxidation and antioxidant enzyme activity of maize plants under temperature stress. Mycorrhiza. 2010;20(5):325–32.

    Article  CAS  PubMed  Google Scholar 

  34. Xu H, Shao H, Lu Y. Arbuscular mycorrhiza fungi and related soil microbial activity drive carbon mineralization in the maize rhizosphere. Ecotoxicol Environ Saf. 2019;182:109476.

    Article  CAS  PubMed  Google Scholar 

  35. Huang JH, Zeng RS, Luo SM. Preliminary study on the resistance of maize sheath blight induced by am mycorrhizal fungi. Chin J Eco-Agric. 2006;14(03):167–9.

    Google Scholar 

  36. Jang SJ, Kim SS, Bak HY, Yun YB, Kuk YI. Effects of organic acids on paraquat activity in maize. S Afr J Bot. 2019;123:286–92.

    Article  CAS  Google Scholar 

  37. Liu RJ, Luo XS. A new method to quantify the inoculum potential of arbuscular mycorrhizal fungi. New Phytol. 1994;128(1):89–92.

    Article  PubMed  Google Scholar 

  38. Liu JJ, Wei Z, Li JH. Effects of copper on leaf membrane structure and root vigor of maize seedling. Bot Stud. 2014;55:1–6.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  39. Wu D, Xu X, Chen Y, Shao H, Sokolowski E, Mi G. Effect of different drip fertigation methods on maize yield, nutrient and water productivity in two-soils in Northeast China. Agric Water Manag. 2019;213:200–11.

    Article  Google Scholar 

  40. Santander C, Aroca R, Ruiz-Lozano JM, Olave J, Cartes P, Borie F, et al. Arbuscular mycorrhiza effects on plant performance under osmotic stress. Mycorrhiza. 2017;27:639–57.

    Article  CAS  PubMed  Google Scholar 

  41. Chen L, Yang X, Raza W, Li J, Liu Y, Qiu M, et al. Trichoderma harzianum SQR-T037 rapidly degrades allelochemicals in rhizospheres of continuously cropped cucumbers. Appl Microbiol Biot. 2011;89:1653–63.

    Article  CAS  Google Scholar 

  42. Zhou X, Wu F. Vanillic acid changed cucumber. Cucumis sativus L. seedling rhizosphere total bacterial, Pseudomonas and Bacillus spp. communities. Sci Rep-UK. 2018;8:4929.

  43. Gu Y, Wei Z, Wang X, Friman V, Huang J, Wang X, et al. Pathogen invasion indirectly changes the composition of soil microbiome via shifts in root exudation profile. Biol Fert Soils. 2016;52:997–1005.

    Article  CAS  Google Scholar 

  44. Ray S, Mishra S, Bisen K, Singh S, Sarma BK, Singh HB. Modulation in phenolic root exudate profile of Abelmoschus esculentus expressing activation of defense pathway. Microbiol Res. 2018;207:100–7.

    Article  CAS  PubMed  Google Scholar 

  45. Hage-Ahmed K, Moyses A, Voglgruber A, Hadacek F, Steinkellner S. Alterations in root exudation of intercropped tomato mediated by the arbuscular mycorrhizal fungus Glomus mosseae and the Soilborne pathogen fusarium oxysporum f.sp. lycopersici. J Phytopathol. 2013;161:763–73.

    Article  CAS  Google Scholar 

  46. Zhou XG, Wu FZ, Xiang WS. Syringic acid inhibited cucumber seedling growth and changed rhizosphere microbial communities. Plant Soil Environ. 2014;4:158–64.

    Google Scholar 

  47. Guo B, Liu C, Ding N, Fu Q, Lin Y, Li H, et al. Silicon alleviates cadmium toxicity in two cypress varieties by strengthening the exodermis tissues and stimulating phenolic exudation of roots. J Plant Growth Regul. 2016;35:420–9.

    Article  CAS  Google Scholar 

  48. De VFT, Williams A, Stringer F, Willcocks R, McEwing R, Langridge H, et al. Changes in root-exudate-induced respiration reveal a novel mechanism through which drought affects ecosystem carbon cycling. New Phytol. 2019;224:132–45.

    Article  Google Scholar 

  49. Jin Y, Jin J, Wang M, Wang Y, Lu W, Lu K, et al. Effect of plants and their root exudate on bacterial activities during rhizobacterium–plant remediation of phenol from water. Environ Int. 2019;127:114–24.

    Article  CAS  PubMed  Google Scholar 

  50. Liu N, Shao C, Sun H, Liu Z, Guan Y, Wu L, et al. Arbuscular mycorrhizal fungi biofertilizer improves American ginseng (Panax quinquefolius L.) growth under the continuous cropping regime. Geoderma. 2020;363:114155.

    Article  CAS  Google Scholar 

  51. Yu Z, Duan X, Luo L, Dai S, Ding Z, Xia G. How plant hormones mediate salt stress responses. Trends Plant Sci. 2020;25(11):1117–30.

    Article  CAS  PubMed  Google Scholar 

Download references

Acknowledgements

We thank the College of agriculture of Guangxi University for providing experimental sites and instrument support.

Funding

This project is supported by National Natural Science Foundation of China (31760137) and Guangxi Natural Science Foundation (2013GXNSFAA019053).

Author information

Authors and Affiliations

Authors

Contributions

Huang JH and Yang J participated in the experimental design; Wang WQ, Qin SF, Yang ys, sun CY collected experimental materials; Liu L, Liao HL, Pei g participated in the experimental analysis, and Muhammad Z participated in the discussion part of the paper; I participated in the experimental analysis, collected the experimental data, analyzed the experimental data and prepared the manuscript. All of the authors read and approved the manuscript.

Corresponding author

Correspondence to Jinghua Huang.

Ethics declarations

Ethics approval and consent to participate

Not applicable.

Consent for publication

Not applicable.

Competing interests

The authors declare that they have no competing interests.

Additional information

Publisher’s Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Supplementary Information

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated in a credit line to the data.

Reprints and permissions

About this article

Check for updates. Verify currency and authenticity via CrossMark

Cite this article

Ma, J., Wang, W., Yang, J. et al. Mycorrhizal symbiosis promotes the nutrient content accumulation and affects the root exudates in maize. BMC Plant Biol 22, 64 (2022). https://doi.org/10.1186/s12870-021-03370-2

Download citation

  • Received:

  • Accepted:

  • Published:

  • DOI: https://doi.org/10.1186/s12870-021-03370-2

Keywords