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. 2022 Feb 5;22:64. doi: 10.1186/s12870-021-03370-2

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

Junqing Ma 1, Wenqi Wang 1, Juan Yang 1,2, Shengfeng Qin 1, Yisen Yang 1, Chenyu Sun 1, Gen Pei 1, Muhammad Zeeshan 1, Honglin Liao 1, Lu Liu 1, Jinghua Huang 1,2,
PMCID: PMC8817564  PMID: 35123400

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.

Supplementary Information

The online version contains supplementary material available at 10.1186/s12870-021-03370-2.

Keywords: Arbuscular mycorrhizal fungi, Root vigor, Nutrient content, Organic acids

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 [1719], which may be related to the effect of root exudates on soil properties, organic pollutant migration and activity [2022]. 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:

Mycorrhizalcolonizationrate%=colonizationrate1+colonizationrate2+colonizationratenThetotalnumberofrootsegmentsobserved×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:

Reductionstrengthoftetrazoleμgg-1h-1=ReductionoftetrazoliumμgWeightofrootg×Timeh

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.

Fig. 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.

Fig. 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.

Fig. 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

Treatment N (mg plant−1) P (mg plant− 1) K (mg plant− 1)
Root Stem Leaf Grain Root Stem Leaf Grain Root Stem Leaf Grain
V12
 RA 381.12 ± 20.31bc 230.62 ± 17.33b 635.48 ± 20.15bc / 43.29 ± 4.16bc 32.28 ± 2.05b 99.03 ± 1.77a / 138.25 ± 8.48a 194.61 ± 2.48b 396.38 ± 10.99bc /
 CE 414.49 ± 39.26b 263.29 ± 16.71ab 727.74 ± 27.42a / 54.69 ± 2.72a 33.70 ± 1.91b 94.03 ± 1.38a / 154.29 ± 10.35a 214.76 ± 6.48a 493.22 ± 3.47a /
 FM 562.44 ± 25.27a 300.81 ± 10.95a 662.61 ± 25.37ab / 44.44 ± 3.30b 50.72 ± 1.21a 98.76 ± 4.54a / 151.09 ± 7.06a 218.26 ± 3.38a 410.44 ± 8.22b /
 MI 317.98 ± 20.95 cd 226.52 ± 15.00b 680.14 ± 28.88ab / 34.36 ± 1.30 cd 38.13 ± 2.31b 95.52 ± 3.00a / 99.13 ± 8.74b 225.58 ± 2.67a 385.93 ± 2.89c /
 CK 262.83 ± 17.87d 156.75 ± 5.61c 557.28 ± 35.55c / 27.07 ± 2.69d 23.51 ± 2.59c 75.52 ± 1.99b / 89.48 ± 7.89b 146.21 ± 2.36c 334.52 ± 1.68d /
P values 0.0001 0.0003 0.0169 / 0.0007 0.0001 0.0007 / 0.0007 0.0001 0.0001 /
CV(±%) 11.32 9.60 7.41 / 12.37 10.9 4.72 / 12.18 2.99 2.33 /
VT
 RA 573.90 ± 28.86b 273.94 ± 10.45a 861.43 ± 27.44a / 60.44 ± 3.09b 105.82 ± 5.63a 169.74 ± 6.96a / 182.85 ± 7.34a 318.75 ± 4.84a 620.27 ± 19.27c /
 CE 659.7419.94a 236.19 ± 5.98b 829.00 ± 40.04a / 75.95 ± 2.25a 96.39 ± 4.21ab 141.65 ± 5.94b / 198.48 ± 10.55a 303.71 ± 12.20a 870.70 ± 6.66a /
 FM 645.69 ± 18.38a 273.25 ± 10.54a 816.58 ± 38.92ab / 64.23 ± 1.35b 86.64 ± 4.47bc 137.61 ± 3.24b / 135.66 ± 3.45b 262.82 ± 7.75b 801.25 ± 1.73b /
 MI 641.33 ± 11.75a 264.39 ± 11.95ab 797.57 ± 40.43ab / 79.69 ± 1.99a 85.97 ± 4.04bc 126.11 ± 6.39b / 184.57 ± 7.27a 315.55 ± 9.35a 868.46 ± 11.44a /
 CK 431.60 ± 23.46c 255.88 ± 16.56ab 717.59 ± 24.55ab / 60.49 ± 2.08b 79.00 ± 3.27c 105.49 ± 8.12c / 134.88 ± 11.16b 247.61 ± 10.11b 632.22 ± 17.03c /
P values 0.0001 0.2050 0.1223 / 0.0002 0.0120 0.0005 / 0.0006 0.0007 0.0001 /
CV(±%) 6.29 7.34 7.34 / 5.58 8.2 8.11 / 8.34 5.38 2.80 /
R1
 RA 579.79 ± 41.04a 207.77 ± 10.05bc 672.99 ± 6.13a / 52.30 ± 3.39a 84.65 ± 1.93c 133.31 ± 4.17a / 139.73 ± 1.83b 228.52 ± 2.84b 540.05 ± 7.89a /
 CE 590.17 ± 7.38a 238.35 ± 10.34ab 605.41 ± 20.86ab / 54.15 ± 5.37a 114.42 ± 3.12a 134.24 ± 7.39a / 154.56 ± 4.88b 227.85 ± 1.67b 483.31 ± 10.75b /
 FM 552.94 ± 14.29a 231.30 ± 12.95ab 613.44 ± 32.51ab / 51.50 ± 1.36a 99.11 ± 4.00b 101.41 ± 3.83b / 216.11 ± 6.46a 235.80 ± 3.94b 455.60 ± 9.23c /
 MI 320.29 ± 6.83b 263.18 ± 11.81a 600.28 ± 29.69ab / 45.38 ± 1.13a 116.92 ± 4.33a 137.21 ± 5.96a / 145.00 ± 2.15b 318.04 ± 10.06a 502.60 ± 3.03b /
 CK 309.49 ± 9.97b 193.44 ± 10.69c 571.83 ± 18.80b / 47.88 ± 1.15a 69.87 ± 3.63d 103.04 ± 4.43b / 137.50 ± 9.93b 188.12 ± 8.84c 407.33 ± 5.67d /
P values 0.0001 0.0060 0.1100 / 0.3008 0.0001 0.0010 / 0.0001 0.0001 0.0001 /
CV(±%) 5.63 7.09 6.20 / 8.28 6.21 7.29 / 5.60 3.99 2.67 /
R2
 RA 363.93 ± 20.82a 396.64 ± 14.96d 453.24 ± 27.72c / 66.09 ± 4.18a 333.52 ± 4.55b 125.73 ± 4.10b / 292.66 ± 9.16b 648.10 ± 3.98b 552.82 ± 4.14a /
 CE 297.65 ± 10.88bc 884.62 ± 33.42a 506.31 ± 24.44c / 61.33 ± 2.81ab 314.23 ± 5.21bc 98.55 ± 3.98c / 295.55 ± 3.39b 651.59 ± 2.57b 495.71 ± 4.93c /
 FM 272.98 ± 15.69c 627.30 ± 27.67c 591.88 ± 13.49b / 55.20 ± 3.39b 300.70 ± 6.31c 107.42 ± 2.53c / 328.90 ± 5.03a 579.48 ± 4.70c 491.66 ± 2.02c /
 MI 314.27 ± 4.98b 796.67 ± 19.09b 776.05 ± 42.63a / 58.02 ± 1.26ab 390.85 ± 11.38a 137.77 ± 7.06a / 248.46 ± 5.27c 676.66 ± 7.25a 532.75 ± 2.29b /
 CK 285.39 ± 3.81bc 465.13 ± 27.74d 447.00 ± 16.54c / 53.31 ± 4.12b 214.76 ± 9.68d 98.52 ± 5.81c / 164.60 ± 13.92d 466.76 ± 6.83d 394.05 ± 5.98d /
P values 0.0047 0.0001 0.0001 / 0.1268 0.0001 0.0001 / 0.0001 0.0001 0.0001 /
CV(±%) 6.25 7.04 7.76 / 9.33 4.34 3.24 / 5.67 1.51 1.42 /
R4
 RA 460.18 ± 17.27a 492.49 ± 15.83a 325.48 ± 9.38b 669.94 ± 35.73c 53.10 ± 2.52a 363.28 ± 4.48c 120.15 ± 4.82b 230.58 ± 4.24b 249.72 ± 7.85b 1263.62 ± 23.14ab 460.57 ± 11.13d 167.36 ± 1.98c
 CE 429.83 ± 21.30ab 434.38 ± 35.33ab 316.19 ± 24.83b 769.54 ± 13.67b 50.62 ± 0.13a 447.22 ± 6.36a 93.68 ± 9.63bc 246.00 ± 6.02a 267.81 ± 4.32a 1283.46 ± 33.51ab 549.96 ± 8.42c 197.50 ± 5.86b
 FM 347.36 ± 32.14c 375.62 ± 40.90b 397.27 ± 18.66a 734.79 ± 20.12bc 51.24 ± 3.14a 392.35 ± 8.50b 167.65 ± 14.44a 171.80 ± 1.54c 230.85 ± 4.11c 1216.85 ± 19.95b 611.02 ± 5.28b 184.30 ± 6.39b
 MI 364.75 ± 17.23bc 360.42 ± 13.87bc 352.82 ± 7.17ab 913.40 ± 24.23a 50.59 ± 1.93a 325.32 ± 7.56d 183.69 ± 6.45a 255.76 ± 4.85a 258.92 ± 6.41ab 1318.86 ± 24.13a 637.11 ± 2.78a 224.27 ± 6.13a
 CK 387.22 ± 11.33bc 276.95 ± 14.79c 326.69 ± 22.78b 563.87 ± 23.25d 47.50 ± 2.21a 248.60 ± 12.15e 89.40 ± 6.52c 122.57 ± 2.84d 203.37 ± 4.13d 931.98 ± 9.84c 395.37 ± 2.94e 124.443.45d
P values 0.0194 0.0022 0.0557 0.0001 0.5419 0.0001 0.0001 0.0001 0.0001 0.0001 0.0001 0.0001
CV(±%) 8.92 10.88 8.47 5.76 6.78 4.17 11.67 3.26 3.27 3.11 1.60 4.55

The five parts in Table 1 are the five growth stages of maize, which are V12 (twelve-leaf stage), VT (tasseling stage), R1 (silking stage), R2 (blister stage), and R4 (dough stage stage). Each growth stage included five treatments, namely RA (maize inoculated with R. aggratus), CE (maize inoculated with C. etunicatum), FM (maize inoculated with F. mosseae), MI (maize inoculated with the above three kinds of AMF), and CK (maize without AMF inoculation). Lower case letters in figures differently indicate significant differences between treatments (p<0.05)

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.

Fig. 4

Primary chromatograms of 10 organic acids standards

Fig. 5.

Fig. 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.

Fig. 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.

Supplementary Information

Additional file 1. (15.5KB, xlsx)

Acknowledgements

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

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

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.

Funding

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

Availability of data and materials

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

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.

Footnotes

Publisher’s Note

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Contributor Information

Junqing Ma, Email: mjq130138@163.com.

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References

  • 1.Johnson NC, Graham JH, Smith FA. Functioning of mycorrhizal associations along the mutualism-parasitism continuum. New Phytol. 1997;135:575–586. [Google Scholar]
  • 2.Koide RT, Mosse B. A history of research on arbuscular mycorrhiza. Mycorrhiza. 2004;14:145–163. doi: 10.1007/s00572-004-0307-4. [DOI] [PubMed] [Google Scholar]
  • 3.Kivlin SN, Hawkes CV, Treseder KK. Global diversity and distribution of arbuscular mycorrhizal fungi. Soil Biol Biochem. 2011;43:2294–2303. [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;40:174–181. [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;172:536–543. doi: 10.1111/j.1469-8137.2006.01846.x. [DOI] [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;20:1043–1053. doi: 10.1111/ele.12802. [DOI] [PubMed] [Google Scholar]
  • 7.Xu J, Liu S, Song S, Guo H, Tang J, Yong JWH, Ma Y, Chen X. Arbuscular mycorrhizal fungi influence decomposition and the associated soil microbial community under different soil phosphorus availability. Soil Biol Biochem. 2018;120:181–190. [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;30:455–466. doi: 10.1007/s00572-020-00962-y. [DOI] [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;111:487–492. doi: 10.1016/j.mycres.2007.02.007. [DOI] [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. doi: 10.1093/aob/mct258. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11.Sun C, Wang D, Shen X, Li C, Liu J, Lan T, Wang W, Xie H, Zhang Y. 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. [Google Scholar]
  • 12.Tian K, Kong X, Yuan L, Lin H, He Z, Yao B, Ji Y, Yang J, Sun S, Tian X. Priming effect of litter mineralization:the role of root exudate depends on its interactions with litter quality and soil condition. Plant Soil. 2019;440:457–471. [Google Scholar]
  • 13.Coskun D, Britto DT, Shi W, Kronzucker HJ. How plant root exudates shape the nitrogen cycle. Trends Plant Sci. 2017;22:661–673. doi: 10.1016/j.tplants.2017.05.004. [DOI] [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;60:2100–2112. doi: 10.1093/pcp/pcz108. [DOI] [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;228:253–264. [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;3:491–498. doi: 10.1093/mp/ssq004. [DOI] [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;20:513–527. doi: 10.1631/jzus.B1900188. [DOI] [PMC free article] [PubMed] [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. [DOI] [PMC free article] [PubMed]
  • 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):920–926. doi: 10.1016/s1001-0742(08)62362-1. [DOI] [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. doi: 10.1016/j.chemosphere.2019.124920. [DOI] [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;48:175–190. [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;354:335–345. [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. doi: 10.1371/journal.pone.0049273. [DOI] [PMC free article] [PubMed] [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. [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;42:473–483. [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. [DOI] [PMC free article] [PubMed]
  • 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. [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;337:749–757. [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):705–709. [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):185–190. doi: 10.1007/s00572-002-0170-0. [DOI] [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. doi: 10.1016/j.plantsci.2016.09.010. [DOI] [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):325–332. doi: 10.1007/s00572-009-0285-7. [DOI] [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. doi: 10.1016/j.ecoenv.2019.109476. [DOI] [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):167–169. [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;123:286–292. [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. doi: 10.1111/j.1469-8137.1994.tb03990.x. [DOI] [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. doi: 10.1186/s40529-014-0047-5. [DOI] [PMC free article] [PubMed] [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;213:200–211. [Google Scholar]
  • 40.Santander C, Aroca R, Ruiz-Lozano JM, Olave J, Cartes P, Borie F, Cornejo P. Arbuscular mycorrhiza effects on plant performance under osmotic stress. Mycorrhiza. 2017;27:639–657. doi: 10.1007/s00572-017-0784-x. [DOI] [PubMed] [Google Scholar]
  • 41.Chen L, Yang X, Raza W, Li J, Liu Y, Qiu M, Zhang F, Shen Q. Trichoderma harzianum SQR-T037 rapidly degrades allelochemicals in rhizospheres of continuously cropped cucumbers. Appl Microbiol Biot. 2011;89:1653–1663. doi: 10.1007/s00253-010-2948-x. [DOI] [PubMed] [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. [DOI] [PMC free article] [PubMed]
  • 43.Gu Y, Wei Z, Wang X, Friman V, Huang J, Wang X, Mei X, Xu Y, Shen Q, Jousset A. Pathogen invasion indirectly changes the composition of soil microbiome via shifts in root exudation profile. Biol Fert Soils. 2016;52:997–1005. [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;207:100–107. doi: 10.1016/j.micres.2017.11.011. [DOI] [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;161:763–773. [Google Scholar]
  • 46.Zhou XG, Wu FZ, Xiang WS. Syringic acid inhibited cucumber seedling growth and changed rhizosphere microbial communities. Plant Soil Environ. 2014;4:158–164. [Google Scholar]
  • 47.Guo B, Liu C, Ding N, Fu Q, Lin Y, Li H, Li N. Silicon alleviates cadmium toxicity in two cypress varieties by strengthening the exodermis tissues and stimulating phenolic exudation of roots. J Plant Growth Regul. 2016;35:420–429. [Google Scholar]
  • 48.De VFT, Williams A, Stringer F, Willcocks R, McEwing R, Langridge H, Straathof AL. Changes in root-exudate-induced respiration reveal a novel mechanism through which drought affects ecosystem carbon cycling. New Phytol. 2019;224:132–145. doi: 10.1111/nph.16001. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 49.Jin Y, Jin J, Wang M, Wang Y, Lu W, Lu K, Zhang L, Jiang Q, Sun S, Cao Q, Xiao M. Effect of plants and their root exudate on bacterial activities during rhizobacterium–plant remediation of phenol from water. Environ Int. 2019;127:114–124. doi: 10.1016/j.envint.2019.03.015. [DOI] [PubMed] [Google Scholar]
  • 50.Liu N, Shao C, Sun H, Liu Z, Guan Y, Wu L, Zhang L, Pan X, Zhang Z, Zhang Y, Zhang B. Arbuscular mycorrhizal fungi biofertilizer improves American ginseng (Panax quinquefolius L.) growth under the continuous cropping regime. Geoderma. 2020;363:114155. [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):1117–1130. doi: 10.1016/j.tplants.2020.06.008. [DOI] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Additional file 1. (15.5KB, xlsx)

Data Availability Statement

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


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