Sandy Mitigation: 17 Fan Plants & Adjacent Tunnels

Outline

Beach plum (Genus Prunus maritima) is an ornamental engraft, famous for its strong salt and drought stress tolerance. However, the poor growth rate of transplanted seedlings has badly qualified its application in salinized soil. This study investigated the effects of vaccination with arbuscular mycorrhizal fungus (AMF), Funneliformis mosseae, and phosphate-solubilizing fungus (PSF), Apophysomyces spartima, on the growth, nutrient (N, P, and K) ingestion, and photosynthesis of beach plum under saline (170 mM NaCl) and not-saline (0 mM NaCl) conditions. We aimed to find measures to increase the rate of growth of beach plum in saline-alkali solid ground and to understand the reasons for this increase. The results showed that salinization adversely struck settlement by AMF merely positively increased PSF populations (increased by 33.9–93.3% over non-NaCl treatment). The dual application of AMF and Popular Struggle Front mitigated the effects of salt stress happening all growth parameters and nutrient uptake, importantly for roots (dry weight and P and N contents increased by 91.0%, 68.9%, and 40%, respectively, over non-NaCl handling). Salinization caused significant reductions in net chemical process rank (P n), stomatal conductance (G s ), transpiration rate (E), and animate thing Colorado2 concentration (C i) apprais, piece vaccination with AMF and PSF inoculations significantly abated so much reductions. The maximum efficiency of photosystem II (PSII) (Fv/Fm), the chemistry extinction coefficient (qP), and the nonphotochemical quenching (NPQ) values were affected little past inoculation with AMF, PSF, or some under non-NaCl treatments. However, plants inoculated with AMF and/Oregon PSF had high Fv/Fm, qP, and ะคPSII values (increased by 72.5–188.1%) than the control nether NaCl treatment, but non a high NPQ apprais. We over that vaccination with AMF or PSF increased nutrient uptake and landscaped the gas-change and Chl fluorescence parameters of beach plum under salt stress environment. These effects could be strengthened by the combination of AMF and PSF, specially for nutrient uptake, radical growth, and P n, thereby alleviating the harmful effects of NaCl stress on beach plum bush growth.

Introduction

Soil salinization is a global upsho that degrades rural solid ground and leads to reduced agricultural yields. IT has been estimated that saline soils account for about 8% of the Earth's surface and are increasing globally1. In these areas, planting crops or fruit trees adapted to alkali-saline soil has promising prospects. Beach plum (Prunus maritima) is a multi-stemmed and deciduous shrub with an spare-long flowering period (more than three months) and rich, edible fruit2. Beach plum has an extremely strong ability to stomach salt and drouth stress and grows on the eastern coast of the U.S.. In 2001, it was start introduced to China aside Nanjing University. Although the survival order is soaring for Prunus maritima in salinized soil, the poor ontogenesis rate of transplanted seedlings had seriously restricted its application in salinized soil in China3.

It is well known that the uptake of mineral nutrients by underground roots and the efficiency of photosynthesis of surface leaves are "seed" forces for plant growth. High concentrations of ions (Na+, Cl, Soh4 2−) in saline soils accumulate in works cells and inhibit alimental (e.g., atomic number 7, phosphorus, and potassium) consumption4 and photosynthesis5. In fact, salt was establish to inhibit specific enzymes involved in the synthesis of photosynthetic pigments, resulting in the decrease of chlorophyll content6. Salt stress nates besides cause significant disturbance to chlorophyll fluorescence. The change of rapid chlorophyl fluorescence can reflect the change of photosynthetic electron transfer and the function and stability of photosystem II (PSII)7. It is widely regarded Eastern Samoa an important parameter for diagnosing the operation of the photosynthetic apparatus in plants and analyzing the mechanism of plant response to stress8.

The introduction of arbuscular mycorrhizal fungus (AMF), Funneliformis mosseae (formerly called Glomus mosseae), to sites with saline soils whitethorn improve the salt tolerance and growth of plants9. Settlement of plant roots and soils by AMF could promote plant nutrient skill by increasing available Phosphorus (P), hydrolyzable N (N), living thing topic subject matter, and individual enzyme activities in ground10,11. The application of mycorrhizal inoculants could also improve the photosynthesis of plants by accretionary Chl content5, transpiration value (E), and stomatal conductance (G s ) and reducing Na+ and Cl uptake5,12,13,14 in legion plants nether salt stress. Inoculation of plants with phosphate-solubilizing fungus (PSF), Apophysomyces spartima, is also applied for saline soil restoration because it can gain P handiness in soils fertilized with sway phosphates15. The released P cannot be transferred to the roots by the PSF simply may be taken finished by the external mycelium of the AMF16. Combined AMF and PSF vaccination could also alleviate the effects of salt emphasis on plant growth away enabling greater nutrient absorption, higher ionic accumulation in different root tissues, and maintenance of lower root Na+/K+ when salt is within acceptable limits17.

Therefore, this study investigated the following questions. Can AMF and/or PSF lessen saline-induced interference of growth, nutrient absorption, and photosynthesis parameters in beach plum? How does AM fungi inoculation impart salty tolerance to beach plum?

Results

AMF colonization, PSF populations, and implant biomass of beach plum nether saltiness stress

Salinity had a significant adverse effect (p < 0.01) on the AMF colonization of beach plum and had a promoting impression on PSF populations (magnified by 33.9–93.3% compared to non-NaCl treatment) (Table 1). Mycorrhizal colonization increased 42% and 45% under non-NaCl and NaCl treatments, respectively, in the dually inoculated plants compared to inoculation with AMF alone. PSF populations in soil co-inoculated with some AMF and Popular Struggle Front were 1.67 × 104 and 3.56 × 104 large in the non-NaCl and NaCl treatments, severally, than in soil inoculated with PSF alone.

Table 1 Effects of F. mosseae and/or A. spartima on arbuscular mycorrhizal fungi (AMF) settlement, phosphate-solubilizing fungus (PSF) populations, and growth parameters of beach plum bush under saline and non-saline conditions.

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The wallop of salinity was more noticeable in shoots (parched weight reduced aside 40%) than roots (dry weight reduced by 20%), which resulted in increasing root/shoot dry weight ratios in Prunus maritima (Shelve 1). The application of AMF and PSF separately or in combination improved shoot and root growing affected past salt. The dual application of AMF and PSF obviously alleviated the effects of salt stress on complete increment parameters, significantly for theme growth (dry weight increased by 91.1% compared to non-NaCl; p < 0.01).

Changes in nutrient content of Prunus maritima under salt stress

Salinity had an contrary effect on P table of contents in the roots of beach plum but had no remarkable effect on the shoots (Fig. 1). Many P was splashed to roots compared to shoots in not-NaCl-bound plants in the same inoculation treatment, patc the lift was observed in NaCl-treated plants (Fig. 1). However, single and combined vaccination with the AMF and PSF powerfully enhanced P table of contents in both roots and shoots (p < 0.01). AMF + PSF discussion exhibited the greatest effects on P contents in the roots and shoots, besides as on the unconditional P table of contents in plants at 170 millimeter NaCl.

Figure 1
figure1

Personal effects of F. mosseae and/or A. spartima on the N, P, and K contents of beach plum under salty and not-saline conditions. The values of from each one parameter labeled by antithetical letters indicate significant differences assessed by Isadora Duncan's test after performing a three-way MANOVA (p < 0.05). ns non-significant; *significant at p < 0.05; **significant at p < 0.01.

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Compared to not-inoculated plants, inoculation with AMF, PSF, or both significantly improved N concentrations regardless of NaCl stress (Fig. 1, p < 0.01). N accumulation was higher in shoots than in roots of the same vaccination treatment (Figure. 1, p < 0.01). Among NaCl-treated plants, co-inoculated plants showed the highest N concentrations in the roots and shoots, and the total N capacity also supported this final result. Salinity exhibited no more significant effects on N contents in the shoots or roots of non-inoculated or separately inoculated plants (p > 0.05).

NaCl stress reduced K contents in the roots merely stirred up accrual in the shoots compared to unemphatic plants (Common fig. 1). Inoculation with AMF, PSF, or both significantly promoted K accumulation in the roots and shoots regardless of salt stress (p < 0.05). Among NaCl-hardened plants, PSF-treated plants showed the highest K assiduity in the shoots (359.7 atomic number 12·kg−1 dry weightiness (DW)) and the lowest values in the roots (43.6 mg·kg−1 DW), and co-inoculated plants showed the highest complete K concentrations (111.6 mg·kg−1 DW).

Changes in photosynthetic parameters of beach plum bush under salt stress

The net photosynthetic rate (P n), orifice conductance (G s ), and transpiration rate (E) were high in inoculated plants than in non-inoculated ones at 0 millimeter NaCl, while a lower intercellular CO2 concentration (C i) value was observed in inoculated plants. Salinization caused significant (p < 0.05) reductions in P n, G s , and E values and a lower C i value, while inoculation with AMF, Popular Struggle Front, or some significantly abated much reductions (p < 0.05, Al-Jama'a al-Islamiyyah al-Muqatilah bi-Libya. 2). The most effective handling was inoculation with AMF and PSF, and the AMF inoculation treatment yielded P n, G s, C i, and E values close to the PSF vaccination treatment (p < 0.05, Fig. 2). Among NaCl-dressed plants, plants atomic number 27-inoculated with AMF and PSF had the highest P n, G s , and E values (increased away 152.1%, 272.7%, and 94.3% compared to only NaCl punctuate, respectively) and the lowest C i evaluate (decreased by 65.5% compared to only NaCl strain).

Figure 2
figure2

Effects of F. mosseae and/or A. spartima on the photosynthetic parameters of beach plum under saline and non-saline conditions. Last photosynthetic rate (P n), animate thing Centennial State2 assiduousness (C i), aperture conductance (G s ), and transpiration rate (E). The values of each parametric quantity labeled by different letters indicate significant differences assessed by Duncan's test after performing a three-way MANOVA (p < 0.05). ns non-significant; *significant at p < 0.05; **significant at p < 0.01.

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Changes in Chl easygoing, Fv/Fm, ะคPSII, qP, and NPQ of beach plum under salt stress

The maximum efficiency of PSII (Fv/Fm), photochemical extinction coefficient (qP), and nonphotochemical quenching (NPQ) values were affected little by vaccination with AMF, PSF, or both under non-NaCl treatments (p < 0.05, Fig. 3). In contrast, sole and combined inoculation with the AMF and PSF strongly enhanced the Chl content (multiplied by 24.3⁠–87.8% compared to the control) and genuine quantum yield of PSII photochemistry (ะคPSII) value. Salinization caused a significant decrease in Chl content, Fv/Fm, qP, and ะคPSII values and an step-up in NPQ value, while inoculation with AMF, PSF, or both significantly abated such reductions (p < 0.05, Fig. 3). Compared with the NaCl discussion unequaled, plants co-inoculated with AMF and PSF had the highest Fv/Fm, qP, and ะคPSII values (augmented by 72.5%, 102.2%, and 188.1%, severally) and lowest NPQ value.

Physique 3
figure3

Effect of F. mosseae and/surgery A. spartima on the chlorophyl fluorescence parameters of beach plum under saline and non-salty conditions. The values of all parameter labeled by different letters indicate significant differences assessed by Duncan's test after performing a many-sided MANOVA (p < 0.05). ns non-significant; *large at p < 0.05; **significant at p < 0.01.

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Corpus component analysis

Principal component analysis (PCA) accounted for all the parameters of the different treatments. Two independent components accounted for 81% of the variability observed in the data, with 62% for PC1 and 19% for PC2 (Fig. 4). Inoculation with AMF or Popular Struggle Front had standardised effects regardless of NaCl stress, but the combination of the two fungi was more effective. Under the non-saline condition, PCA indicated there were positive correlations among the ontogenesis, fungal infection, nutrient (N, P, and K), Chl content, photosynthetic parameters, and Chl fluorescence parameters but not for Ci, NPQ, or root/shoot dry weight ratio. PCA also addicted the Gram-negative impact of SALT immersion along these parameters, merely the combination of AMF and Popular Struggle Front could mitigate these effects, especially for nutrient uptake, root growth, and P n (Libyan Fighting Group. 4).

Figure 4
figure4

Principal component analysis of the affected parameters of different treatments of beach plum under saline and non-saline conditions. S, Salinity; AMF, arbuscular mycorrhizal fungi; Popular Struggle Front, inorganic phosphate-solubilizing fungi; Wshoot, pullulate dry slant; Wroot, etymon dry weighting; Wratio, settle down/dissipate dry weight ratio; Pshoot, element uptake of shoots; Proot, phosphoric consumption of roots; Ptotal, phosphorous intake of the total plant; Nshoot, nitrogen uptake of shoots; Nroot, N consumption of roots; Ntally, nitrogen ingestion of the total engraft; Kscoot, atomic number 19 uptake of shoots; Kroot, K uptake of roots; Ktotal, potassium uptake of the total plant; Chl, chlorophyll; C i, intercellular CO2 concentration; E, transpiration rate; Fv/Fm, the maximum quantum yield of PSII in dark-modified state; G s , stomatal conductance; NPQ, nonphotochemical quenching; P n, take-home photosynthetic order; qP, photochemical quenching coefficient; and ะคPSII, effective quantum yield of PSII.

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Discussion

Salinization adversely moved colonisation by AMF just positively hyperbolic PSF populations

Our results showed that salinity reduced the ability of F. mosseae to colonise beach plum roots. This finding was consistent with previous reports that concluded that salinity hinds the spore sprouting, colonization ability, and the increment of AMF hyphae18,19. Our results showed that AMF conjunct with PSF promoted mycorrhizal root colonization under NaCl emphasise (Table 1). Combined inoculation with AMF and PSF increased the AMF colonization rate. This May represent largely attributed to the increase of grease-fat-soluble P caused by PSF in saline soil, which promoted the rapid colonization of mycorrhiza and increased the distribution, distance, and survival rate of the foreign fungal mycelium in saline filth20. The vaccination of AMF and PSF also significantly increased the soil PSF population, possibly payable to the carbonaceous substances released by mycorrhized plants, which served arsenic a C source for PSF in the rhizosphere soil21.

AMF and PSF mitigated the effects of salt accent along nutrient consumption, significantly for roots

Carbon monoxide gas-inoculation with AMF and Popular Struggle Front had a synergistic effect on the increase in plant DW. Similar personal effects birth been found in Leucaena leucocephala 22 and Kostelelzkya virginica 4. A. spartima was isolated from the top 0–10 centimeter of soil from a community of Spartina alterniflora in North Jiangsu Province and has been proven to be an timesaving phosphate-solubilizing fungus11. The donation of the PSF to ontogenesis promotion was probably referable increasing the soil P pool available for AM fungal extraradical hyphae to pass IT on to the plants23 (Ficus carica. 1). In this study, one reason out for the increase in carbon monoxide gas-inoculated plant DW was thought to be the absorbance of more P from the soil and its accumulation toward the shoots, resulting in increased shoot and root sec burthen (Table 1; Fig. 1).

AMF and Popular Struggle Front have a interactive core on the dissolution and absorption of P 10,11,24. PSF increases the soil P pocket billiards that can be used by AMF extraradical hyphae to deliver P to plants25. AMF produces extrametrical mycelia, which reduce the distance between P and AMF and tolerate plants to select dormie P more well16. However, in the 170 mM NaCl discourse, more P was allocated to the shoots than that to roots in the same inoculation discussion (Fig. 1). The inhibitory effects of salt stress on shoot emergence were greater than those happening root growing (Board 1), which is consistent with Qiu et al.11 and Ben-Laouane et al.26 but not with Ait-El-Mokhtar et al.17 SALT stress had different effects on the root and shoot growth of different sorgho varieties10. Is the varying sensibility of the roots and stems of different plants to emphasis related to their particular mechanisms of coping with stress? This interview will require U.S. to explore more anatomical and physiological indicators in the future.

Salinity interferes with the attainment and utilization of N, leading to a declension in institut growth27. However, N content in the shoots was not significantly influenced past 170 millimetre NaCl, while N substance in the roots showed an upward trend in the present field (Fig. 1). This may represent an important chemical mechanism for this halophyte to relieve the symptoms of severe salt accentuat. Regardless of NaCl focus, single inoculation of AMF and co-vaccination with PSF can greatly step-up N accumulation in the roots and shoots of beach plum (Table 1; Fig. 1). AMF can addition the utilization of different forms of N aside plants28, and IT has been proved that AMF directly absorbs N and transfers it to the host rootage29. In accession, AMF and PSF may kick upstairs urease natural process in the soil, thus catalyzing urea hydrolysis to release ammonia or ammonium ions18.

When common salt content in the soil is at a high level, plants run to absorb Sir Thomas More Na, resulting in reduced K absorption30. Uniform inoculation with AMF and co-inoculation with PSF could, A Abdel-Fattah and Asrar31 also bristle-pointed out, significantly elevat K accumulation in the roots and shoots compared with non-inoculated plants (Fig. 1). This may be because AM roots explored a big volume of soil though the extraradical mycelium, which increased root exudation or altered rhizosphere pH scale, thereby increasing K exercis32. However, PSF-processed plants had the lowest K denseness in their roots subordinate NaCl stress (Fig. 1). The reason for this is unclear, but the mass propagation of PSF may contend with the root system for K absorption.

Plants inoculated with AMF and/or PSF showed a positive impression on photosynthesis and Chl fluorescence parameters

High chlorophyl content, P n, G s , and E values, and take down C i values were perceived in plants inoculated with AMF, PSF, or some regardless of NaCl stress. This agreed with the results of other studies11,33 (Fig. 2). Mycorrhizal inoculation enhances phosphorus and magnesium uptake and reduces atomic number 11 concentrations in the engraft; this in turn increases Chl message and improves the boilersuit performance of mycorrhizal plants5. Caravan hideaway Driessche34 detected a close relationship between some nutrients (N, Mg, and Fe) and chlorophyll and reported that an addition in those nutrients could contribute to a stimulation of the deductive reasoning of chlorophyll and hence the photosynthetic capacity. The improvement of gas-exchange parameters in the inoculated plants has been linked to alterations of host plants with the increased nutrient uptake 6,35,36 and would unremarkably translate into inflated photosynthesis37. K plays an important office in porta movements and protein synthesis38. In this study, the increase of K table of contents in co-inoculated plants is attributed to the accumulation of more K in shoots, resulting in increased g s values (Figs. 1, 2). These four positive personal effects, P n, G s , C i , and E, English hawthorn also take in accounted for the enhanced plant growth of inhabited plants, most probably by enhancing CO2 fixation low-level salt stress39. These also demonstrated that one of the factors resulting in high dry mass accumulation in inoculated plants, particularly in co-inoculated plants, was the hyperbolic capacity for Carbon monoxide2 absorption and the decreased intercellular CO2 concentration compared to those of non-inoculated plants subordinate NaCl sress40.

The parameters of Chl fluorescence accurately reflect photosynthetic ability and energy conversion efficiency7. Under salt stress, a reduction in values of Fv/Fm, qP, and ะคPSII is often an indicator of photoinhibition or another rather injury to PSII components41,42,43. Inoculations with AMF increased the salt tolerance of beach plum by reducing the decline in Fv/Fm, ฮฆPSII, and qP and the increase in NPQ caused away NaCl accentuate (Fig. 3). This indicated that an AMF symbiotic relationship can enhance the efficiency of excitation Energy Department capture by chloroplasts and increase the photochemical capacity of PSII in light-colored-adapted leaves44. Co-vaccination with AMF and PSF had a synergetic effect on improvement in the parameters of Chl fluorescence subordinate NaCl stress (Fig. 3). Our data indicated that plants Centennial State-inoculated with AMF and PSF had the highest photochemical efficiency for Conscientious objector2 fixation and solar energy utilization and that co-vaccination would importantly reduce the short-induced damage due to saltiness compared to a single inoculation with AMF or Popular Struggle Front (Fig. 3). Kaschuk et Camellia State.45 reported that AM mutualism enhancing PSII and reduction NPQ may constitute bound up the carbon sink stimulation of AMF mutualism. Zhang et aluminum.10 ground that beaver bean carbon monoxide gas-inoculated with AMF and PSF enlarged the C pool of coastal saline ground much much a single inoculation of AMF or PSF. No information is available on the effects of PSF happening Chl fluorescence parameters under NaCl stress to particular date. PSF inoculation may relieve the deleterious effects of salt accent along Chl fluorescence parameters by facultative greater nutrient (N, P, and K) absorption10 (Fig. 1). Sure enough, the hypothesis that inoculations with PSF could improve plant Chl fluorescence parameters under NaCl stress also of necessity further study. Still, among non-NaCl-treated plants, Fv/Fm, qP, and NPQ values were not significantly different in the inoculated plants compared to non-inoculated ones (Fig. 3). These parameters are sensitive to stress6, and the plants were non subjected to adverse conditions under the consideration of no stress.

Conclusion

Salt stress reduced growth, alimentary (N, P, and K) intake, and chemical change and chlorophyll fluorescence parameters in Prunus maritima. The application of AMF and PSF separately inflated growth parameters, chemical change efficiency, and the tightness of photosynthetic pigments below saline solution conditions by enhancing N, P, and K ingestion. These personal effects could be reinforced by the synergy of AMF and PSF, specially for nutrient uptake, root maturation, and P n. Our findings highlight the importance of considering the twofold application of AMF and PSF to alleviate the hurtful effects of beach clean growing in salinized soils.

Material and methods

Plant materials

A total of 3000 new, growing, and semi-lignified branches of Prunus maritima (Prunus maritima), each 10-cm-long and 0.5–1.0 cm in diameter with deuce buds, were collected from the Agricultural Rubber-necking Garden, Lishui County, Jiangsu, in March 2022. All cuttings were swaybacked in 1% (w/w) captan (Red Sun Group, Nanjing, China) for 10 minute as a preventative measure against mildew. The substrate used was a 1:1 (v/v) mixture of quartz sand and nutrient bemire (a commercial soil purchased from the Red Sunday Aggroup, Nanjing, China), which had been sterilized away autoclaving twice for 1 h at 121 °C. The nutrient begrime had the following characteristics: pH, 7.05; electric conductivity (EC), 0.71 Doctor of Science·m−1; organic matter, 13.5 g·kg−1; hydrolyzable N, 48.0 atomic number 12·kg−1; in stock P, 14.7 mg·kg−1; and visible K, 14.8 g·kg−1.

Fungal inoculum

The mycorrhizal fungus used was F. mosseae, motley in the loose soils with AMF spores, hyphae, and settled maize root fragments. The original inoculum (BGCJX01) was provided aside the Establish of Plant Nutriment and Fertilizers, Chinese Honorary society of Agriculture. It was separated from the rhizosphere (nonaligned to slightly alkaline) of perfumed Genus Osmanthus fragrans trees in Jiangxi, Taiwan, and was propagated on maize plants flourishing in sandy colly for 10 weeks18. The A. spartima was isolated from the topsoil (0–10 cm) samples of a Spartina alterniflora community of interests in North Jiangsu province. IT had been previously identified as a phosphate-solubilizing fungus that could significantly heighten available P concentrations13. The inoculum of A. spartima was prepared using the method acting of Zhang et al..4 To prepare the liquid inoculum of A. spartima, the initiative was to activate strains happening nutrient agar slants. The fungus was inoculated on solid Martin culture medium (di-K hydrogen orthophosphate 1 g, magnesium sulfate 0.5 g, sodium chloride 11.5 g, peptone 5 g, glucose 10 g, gelose 10 g, 1/30,000 bengal red ink water solution 100 mL, and demineralized water 900 mL), which had been autoclaved for 30 min at 121 °C and then incubated in the wickedness at 28 °C for 4 d. After activation, 3 millilitre sterile water was added to the test tube, and the miscellanea was poured into 50 mL Martin broth (MB), which was then added to 1.15% NaCl; A. spartima was full-grown on a rotating shaker at 180 rpm for 48 h, and this was the starter culture. It was added (5% of volume) to MB. We then added 1.15% NaCl, and the Bachelor of Medicine was cultured along a mover and shaker for 96 h at 180 rpm. At the end, IT contained 2.3 × 105 Colony forming units per mL, and the solution was stored at 4 °C until expend.

Experimental design and biological treatments

The experiment was run for based on a three-factor, cardinal-level randomised block design. One factor, brininess discourse, contained cardinal intensities: 0 and 170 millimeter NaCl. The secondment factor, AMF vaccination, Funneliformis mosseae, restrained two levels: no AMF application (− AMF) and vaccination with AMF (+ AMF). The tertiary element, PSF inoculation, Apophysomyces spartima, enclosed two levels: no PSF application (− Popular Struggle Front) and inoculation with PSF (+ PSF). In total, there were eight treatment combinations, and each was repeated threefold. Each replication consisted of 50 pots with unmatched plant per pot, making 1200 pots in total.

On 10 June 2022, 1200 healthy beach plums plants of similar size (tiptop from 49 to 51 cm, number of leaves from 54 to 56) were transplanted into 30 cm × 20 cm pots, to each one filled with 900 g of cultivation substrate (as in a higher place). Referring to the mixing ratio of inocula and substrate in our previous experiments18, the fungal inocula were added to the supra substrate at a depth of 5 cm with the following design: 10 g F. mosseae inoculum and 10 mL sterile A. spartima inoculum for the AMF treatment; 10 g barren F. mosseae inoculum and 10 cubic centimetre A. spartima inoculum for the PSF handling; 10 g F. mosseae inoculum and 10 millilitre A. spartima inoculum for the AMF + PSF treatment; and 10 g sterile F. mosseae inoculant and 10 mL sterile A. spartima inoculum for the curb treatment (recorded as CK).

From each one pot was placed on a 2-cm-deep tray and placed in a greenhouse under controlled conditions (16 h photoperiod at a light intensity of 220 ยตmol·m–2·s–1 at 28 °C, and 8 h of dark at 18 °C, with the relative humidity kept at 65–85%) on 12 June 2022. All pots were irrigated with distilled water, and the plants were allowed to base for 4 weeks. The pots were and so moire exploitation a varied Hoagland and Arnon45 solution with all nutrients except P. The salinity of the substrate was based on the unemotional mass of the medium and was tested as follows: 3 g of NaCl was dissolved in 300 mL of water supply and poured into each thron evenly three multiplication between day 7 and day 21 to avoid serious osmotic shock and to give a final NaCl concentration of 170 mM. An equal bulk of distilled pee was poured into the four trays without NaCl handling by the same method acting mentioned supra. Any occasional leak was poured backwards into the tray later 1 h, and distilled water was added as necessary to assert the soil moisture level. The pH of the substratum altogether treatments was 7.2. After establishing sharp stress, each pot was watered with 200 milliliter of Hoagland and Arnon nutrient solution every 3 d until day 90.

Plant biomass and nutrient (N, P, K) measurements

After 90 d, three plants were removed randomly from pots and dried in a forced-air oven at 80 °C for 72 h for biomass purpose. The oven-dried samples were sieved through a 0.5-mm sieve. A known mass of the primer coat material was digested in a digestion flaskful containing a triple vitriolic concoction [HNO3:H2SO4:HCl (60%), with a ratio of 10:1:4] to analyze the tot P. P was analyzed using the vanadate-molybdate colorimetric method acting10. Total N was measured in samples of 0.1 g dry mass using the Kjeldahl method46. Each sample was heated in a digestion tube for at to the lowest degree 8 h with stored up sulfuric blistering (98.8%). Distillation of the completely digested samples was carried out using an aqueous solution of Na hydroxide (40%). The extracted ammonium was liquid in 15 cubic centimeter of boric acidic and then automatically titrated with 25 mmol·L–1 sulfuric acid using bromocresol green-methyl crimson mixture as an index number. K concentration was analyzed using an ICP (J-A1100; Jarrell-Ash tree Inc.).

PSF populations and AMF colonization assessment

All plants were extracted from pots on the 30th Clarence Shepard Day Jr. after the beginning of the stress period. Soil samples obtained by tame trembling of the roots were self-collected in sterilized culture dishes and stored at 4 °C until the PSF population analyses using a tenfold nonparallel dilution test subway system technique47. To assess the extent of AMF colonization, the roots of three plants from each treatment were cleansed with 10% (w/v) KOH and tainted with 0.05% (w/v) trypan dirty. The percentage of root length stained and colonized by AMF was estimated according to McGonigle et al.48. The roots of each plant were delve 1-cm-long pieces, and 30 pieces from each plant were examined for their AMF content victimization a compound microscope (NLCD-307, Ningbo Yongxin Phenix Optical Ltd., Ningbo, China) at 100× magnification. A supportive issue for AMF colonization included the presence of vesicles operating theater arbuscules, or the true mycelium within the roots. The percentage of AMF colonization was calculated as follows:

$$ \text{AMF colonisation} (\%) = \text{Inhabited Root segments} / \text{Total root segments} \times 100\%. $$

Blow-exchange parameters measurements

Gas-exchange parameters, including the net photosynthetic rate (P n), intercellular CO2 tightness (C i), porta conductance (G s ), and transpiration rate (E), were measured using a portable open current petrol-switch over scheme LI-6400 (LI-6400, LI-COR, Lincoln, NE, USA) from 08:30 to 11:30 in the dayspring49. The 3rd to 5th leaves from the end of beach plum were used to essay these parameters. The photosynthetically active irradiation was 1200 ยตmol·m–2·s–1, the CO2 concentration was 400 cm3·m–3, the leaf temperature was 25 °C, and the airflow plac was 0.5 dm3·Taiwanese–1.

Chl placid and Chl fluorescence parameters measurements

The 3rd to 5th leaves from the end of beach plum were used to check Chl content and Chl fluorescence parameters. The origin from 50 mg of fresh material was incubated in 5 mil of 80% acetone in the Acheronian at 4 °C. Aft incubation, the extract was understand at 645 nm and 663 nm in a Uvikon 940 spectrophotometer with a apparitional slit width of 1.8 nm. The following parameters were deliberate by the classic convention49: Chl a = 12.7A663 – 2.69A645, Chl b = 22.9A645 – 4.68A663. Further, the same leaves were wont to measure the parameters of Chl fluorescence reported to the methodology of Chen et aluminum.50. The MINI-PAM (MINI-PAM, Waltz, Germany) was utilized to measure the fluorescence induction curvature and the rapid illumination response curve of beach plum leaves under salt accentuat, and in each case, four duplicates of measurement were used. The fluorescence evocation curve methods were as follows: Firstly, plants were kept in Cimmerian for 30 min before measuring. Second, the measuring visible light was yawning (wavelength 650 nm, inflection frequency of 0.6 kHz, photosynthetically active radiation (PAR) to a lesser degree 0.15 ฮผmol·m–2·s–1, and the modulation frequency mechanically switched to 20 kHz when the saturation throb light or actinic light gaping). Finally, F0 was measured. Fm was measured by the vividness pulsate light (continuing 0.8 s, PAR greater than 8000 ฮผmol m–2 s–1). After 40 s, the actinic light was kept (PAR of about 1000 ฮผmol m–2 s–1) on and the saturation pulses light was opened every 30 s. The steady-state fluorescence parameters (Ft) and PAR of the ill-modified sample could be careful when the sampling achieved stable status, and the supreme fluorescence yield (Fm') could be measured nether saturation pulse light. The calculated parameters were arsenic follows: Fv/Fm = (Fm – F0)/Fm, ะคPSII = (Fm' – Ft)/Fm', qP = (Fm' – Ft)/(Fm' – F0), NPQ = (Fm – Fm')/Fm'.

Statistical analytic thinking

Entirely data were statistically analyzed by many-sided multivariate depth psychology of variance (MANOVA) for the primary effects (Salinity, S; AMF inoculation, A; PSF inoculation, P) and their interactions using SPSS 17.0 (IBM Corporation., Armonk, NY, USA), and means were distributed victimization Duncan's mental test at p values < 0.05. Corpus component analysis (PCA) was performed exploitation Unscrambler v. 10.4 (CAMO, Oslo, Norway).

Abbreviations

AM :

Carbuscular mycorrhizal

AMF :

Arbuscular mycorrhizal fungus

PSF :

Inorganic phosphate-solubilizing fungus

Chl :

Chlorophyl

C i :

Living thing CO2 immersion

DW :

Dry weight

E :

Transpiration rate

F0 :

The minimal fluorescence in a dark-adapted state

Fm :

The maximal fluorescence in a dour-adapted state

Fv :

Unsettled fluorescence

Ft :

Steady-body politic fluorescence parameters

Fm' :

Maximum fluorescence yield

Fv/Fm :

The maximal quantum yield of PSII in a dark-adapted state

G s :

Stomatal conductance

NPQ :

Nonphotochemical quenching

PAR :

Photosynthetically active radiation

PSII :

Photosystem II

P n :

Net photosynthetic rate

qP :

Photochemical quenching coefficient

ะคPSII :

Utile quantum yield of PSII

References

  1. 1.

    Estrada, B., Aroca, R., Maathuis, F. J., Barea, J. M. & Ruiz-Lozano, J. M. Arbuscular mycorrhizal fungi native from a mediterranean salty area enhance maize tolerance to brininess through improved ion homeostasis. Plant Cell Environ. 36, 1771–1782 (2013).

    CAS  PubMed  Article  Google Scholar

  2. 2.

    Uva, R. H. &ere; Felon, T. H. Beach plum tree (Prunus maritima Marsh.): Small produce sustainability finished crop variegation and value added products. HortScience 38, 793 (2003).

    Google Scholar

  3. 3.

    Yan, D. L., Wang, G., Fang, K., Zai, X. M. & Qin, P. Introduction, cultivation and utilization of sharp-tolerance beach plumb. Taiwan For. Sci. Technol. 20, 67–69 (2006).

    Google Scholar

  4. 4.

    Zhang, H. S., Wu dialect, X. H. & 51, G. Interactions between arbuscular mycorrhizal fungi and phosphate solubilizing fungus (Mortierella sp.) and their effects on Kostelelzkya virginica growth and enzyme activities of rhizosphere and bulk soils at different salinities. Biol. Fert. Soils 47, 543–554 (2011).

    CAS  Article  Google Scholar

  5. 5.

    Ait-El-Mokhtar, M. et al. Alleviation of prejudicious effects of salt emphasize on go steady palm (Phoenix dactylifera L.) past the application of arbuscular mycorrhizal fungi and/or compost. Front. Sustain. Food Syst. 4, 131 (2020).

    Article  Google Scholar

  6. 6.

    Porcel, R., Redondo-Gรณmez, S. &adenylic acid; Mateos-Naranjo, E. Arbuscular mycorrhizal symbiosis ameliorates the optimum quantum yield of photosystem II and reduces non-chemistry quenching in rice plants subjected to salt stress. J. Set Physiol. 185, 75–83 (2015).

    CAS  PubMed  Article  Google Scholar

  7. 7.

    Sheng, M., Tang, M. & Chen, H. Influence of arbuscular mycorrhizae on photosynthesis and water position of Zea mays plants under salt stress. Mycorrhiza 18, 287–296 (2008).

    CAS  PubMed  Clause  Google Scholar

  8. 8.

    Harbinson, J. Up the accuracy of chlorophyll fluorescence measurements. Set Cell Environ. 36, 1751–1754 (2013).

    PubMed  Article  Google Scholar

  9. 9.

    Zhu, X. C., Song, F. B., Liu, S. Q. & Liu, T. D. Arbuscular mycorrhizae improves photosynthesis and water status of Zea mays L. under drought stress. Plant Grime Environ. 58, 186–191 (2012).

    CAS  Clause  Google Scholar

  10. 10.

    Wang, F., Sun, Y. & Shi, Z. Arbuscular mycorrhiza enhances biomass production and salt tolerance of sweet Sorghum. Microorganisms 7, 289 (2019).

    CAS  PubMed Central  Article  PubMed  Google Scholar

  11. 11.

    Qiu, Y. J. et alii. Mediation of arbuscular mycorrhizal fungi on growth and biochemical parameters of Ligustrum vicaryi in response to saltiness. Physiol. Mol. Plant Pathol. 112, 101522 (2020).

    CAS  Article  Google Scholar

  12. 12.

    Zhang, H. S., Qin, P. & Zhang, W. M. Effects of vaccination of arbuscular mycorrhizal fungus and Apophysomyces spartina on P-uptake of beaver anoint plant (Castor bean plant L.) and rhizosphere soil enzyme activities under salt punctuate. Agri. Sci. Technol. 15, 659 (2014).

    CAS  Google Bookman

  13. 13.

    Ghorchiani, M., Etesami, H. & Alikhani, H. A. Improvement of growth and yield of maize under water system tension past carbon monoxide-inoculating an arbuscular mycorrhizal fungus and a plant growth promoting rhizobacterium together with phosphate fertilizers. Agric. Ecosyst. Surround. 258, 59–70 (2018).

    CAS  Article  Google Learner

  14. 14.

    Augรฉ, R. M., Toler, H. D., Sams, C. E. &adenylic acid; Nasim, G. Hydraulic conductance and water possible gradients in squash leaves showing mycorrhiza-induced increases in stomatal conductance. Mycorrhiza 18, 115–121 (2008).

    PubMed  Article  Google Scholar

  15. 15.

    Sharma, S., Compant, S., Ballhausen, M. B., Ruppel, S. & Franken, P. The interaction between Rhizoglomus irregulare and hyphae affianced orthophosphate solubilizing bacteria increases plant biomass of Solanum lycopersicum. Microbiol. Res. 240, 126556 (2020).

    CAS  PubMed  Article  Google Scholar

  16. 16.

    Vassilev, N., Eichler-Lรถbermann, B. & Vassileva, M. Stress-tolerant P-solubilizing microorganisms. Appl. Microbiol. Biot. 95, 851–859 (2012).

    CAS  Article  Google Scholarly person

  17. 17.

    Ait-El-Mokhtar, M. et al. Use of mycorrhizal fungi in improving tolerance of the go steady palm (Phoenix dactylifera L.) seedlings to salt stress. Sci. Hort. 253, 429–438 (2019).

    Clause  Google Scholar

  18. 18.

    Zai, X. M., Zhu, S. N., Qin, P., Che, L. & Luo, F. X. Effect of Glomus mosseae on chlorophyl content, chlorophyll fluorescence parameters, and chloroplast ultrastructure of beach clean (Prunus maritima) nether NaCl stress. Photosynthetica 50, 323–328 (2012).

    CAS  Article  Google Assimilator

  19. 19.

    Navarro, J. M., Pรฉrez-Tornero, O. &adenosine monophosphate; Morte, A. Alleviation of salt emphasis in citrus seedlings inoculated with arbuscular mycorrhizal fungi depends along the rootstock salt tolerance. J. Plant Physiol. 171, 76–85 (2014).

    CAS  PubMed  Article  Google Scholar

  20. 20.

    Toro, M., Azcon, R. & Herrera, R. Personal effects on yield and nutrition of mycorrhizal and nodulated Pueraria phaseolides exerted by P-solubilizing rhizobacteria. Biol. Fertil. Soils 21, 23–29 (1996).

    Article  Google Bookman

  21. 21.

    Singh, S. & Kapoor, K. K. Vaccination with orthophosphate-solubilizing microorganisms and a vesicular-arbuscular mycorrhizal fungus improves dry matter yield and nutrient uptake by wheat grown in a blonde soil. Biol. Fertil. Soils 28, 139–144 (1999).

    CAS  Article  Google Scholarly person

  22. 22.

    Osorio, N. W. & Habte, M. Synergistic act upon of an arbuscular mycorrhizal fungus and a P solubilizing fungus happening growth and P uptake of Leucaena leucocephala in an Oxisol. Arid Terra firma Res. Manag. 15, 263–274 (2001).

    CAS  Article  Google Learner

  23. 23.

    Khan, M. S., Zaidi, A. & Wani, P. A. Role of phosphate-solubilizing microorganisms in property agriculture—A review. Agron. Hold up Dev. 27, 29–43 (2007).

    Article  Google Student

  24. 24.

    Saxena, J., Saini, A., Ravi, I., Chandra, S. & Garg, V. Consortium of phosphate-solubilizing bacteria and fungi for promotion of growth and yield of chickpea (Cicer arietinum). J. Browse Improv. 29, 353–369 (2015).

    CAS  Article  Google Bookman

  25. 25.

    Smith, S. E. & Read, D. J. Mycorrhizal Mutualism (Academic Weigh, 2008).

    Google Scholar

  26. 26.

    Ben-Laouane, R., Baslam, M., Ait-El-Mokhtar, M., Anli, M. & Meddich, A. Potential of indigenous arbuscular mycorrhizal fungi, rhizobia, and/or green compost as Medicago sativa (Medicago sativa) enhancers under salinity. Microorganisms 8, 1695 (2020).

    CAS  PubMed Central  Article  PubMed  Google Scholarly person

  27. 27.

    Hodge, A., Campbell, C. D. &adenylic acid; Fitter, A. H. An arbuscular mycorrhizal fungus accelerates decomposition and acquires nitrogen directly from organic material. Nature 413, 297–299 (2001).

    ADS  CAS  PubMed  Article  Google Learner

  28. 28.

    Johansen, A., Finlay, R. D. & Olsson, P. A. Nitrogen metabolism of outside hyphae of the arbuscular mycorrhizal fungus Glomus intraradices. New Phytol. 133, 705–712 (1996).

    CAS  Article  Google Scholar

  29. 29.

    Vicente-Sรกnchez, J. et al. Arbuscular mycorrhizal symbiosis alleviates detrimental personal effects of saline reclaimed piss in lettuce plants. Mycorrhiza 24, 339–348 (2014).

    PubMed  Article  CAS  Google Scholar

  30. 30.

    Abdel-Fattah, G. M. & Asrar, A. W. A. Arbuscular mycorrhizal fungous applications programme to improve growth and permissiveness of wheat (Triticum aestivum L.) plants grown in saline soil. Acta Physiol. Plant. 34, 267–277 (2012).

    CAS  Article  Google Assimilator

  31. 31.

    Marschner, P. Rhizosphere biota. In Marschner's Mineral Nutrition of High Plants 3rd edn (ed. Marschner, P.) 369–388 (Academic Press, 2012).

    Chapter  Google Scholar

  32. 32.

    Abd-Allah, E. F. & Egamberdieva, D. Arbuscular mycorrhizal fungi enhance basil tolerance to salt stress through improved physiological and organic process status. Pak. J. Bot. 48, 37–45 (2016).

    Google Scholar

  33. 33.

    Van hideout Driessche, R. Effects of nutrients along blood line performance in the forest. In Asphaltic Nutrition of Conifer Seedlings (male erecticle dysfunction. van den Driessche, R.) 229–260 (CRC Press, 1991).

    Google Scholar

  34. 34.

    Ebel, R. C., Duan, X., Still, D. W. & Augรฉ, R. M. Xylem cosh abscisic acid immersion and stomatal conductance of mycorrhizal Vigna unguiculata in drying dirty. Fresh Phytol. 135, 755–761 (1997).

    CAS  Article  Google Scholar

  35. 35.

    Ruiz-Lozano, J. M. &ere; Aroca, R. Host response to osmotic stresses: Stomatal doings and water use efficiency of arbuscular mycorrhizal plants. In Arbuscular Mycorrhizas: Physiology and Function 239–256 (Springer, 2010).

    Chapter  Google Scholar

  36. 36.

    Birhane, E., Sterck, F. J., Fetene, M., Bongers, F. & Kuyper, T. W. Arbuscular mycorrhizal fungi raise photosynthesis, water use efficiency, and outgrowth of olibanum seedlings under pulsed water availability conditions. Oecologia 169, 895–904 (2012).

    ADS  PubMed  PubMed Central  Article  Google Scholar

  37. 37.

    Evelin, H., Giri, B. & Kapoor, R. Ultrastructural demonstrate for AMF mediate salt stress mitigation in Trigonellafoenum graecum. Mycorrhiza 23, 71–86 (2012).

    PubMed  Article  CAS  Google Scholar

  38. 38.

    Aroca, R. et aluminum. Arbuscular mycorrhizal mutualism influences strigolactone production under salinity and alleviates salt accentuat in lettuce plants. J. Plant Physiol. 170, 47–55 (2013).

    CAS  PubMed  Article  Google Scholar

  39. 39.

    Jungklang, J. Physical and biochemical mechanisms of common salt tolerance in Sesbania rostrata Shoulder and Obem. Ph.D. Thesis (Agric Univ Teckuba, 2005).

  40. 40.

    Baker, N. R. & Rosenqvist, E. Applications of chlorophyl fluorescence can meliorate crop production strategies: Interrogation of future possibilities. J. Exp. Bot. 55, 1607–1621 (2004).

    CAS  PubMed  Article  Google Scholar

  41. 41.

    Nwugo, C. C. & Huerta, A. J. Effects of silicon nutrition on cadmium ingestion, growth and photosynthesis of Timothy Miles Bindon Rice plants exposed to low-level Cd. Plant Soil 311, 73–86 (2008).

    CAS  Article  Google Scholar

  42. 42.

    Henriques, F. S. Leaf chlorophyll fluorescence: Background and fundamentals for plant biologist. Bot. Rev. 75, 249–270 (2009).

    Article  Google Scholar

  43. 43.

    Gong, M. G., Tang, M., Chen, H., Zhang, Q. &adenylic acid; Feng, X. Effects of two Glomus species on the growth and physiological performance of Sophor davidii seedlings under water tenseness. Refreshing For. 44, 399–408 (2013).

    Article  Google Scholar

  44. 44.

    Kaschuk, G., Kuyper, T. W., Leffelaar, P. A., Hungria, M. &ere; Giller, K. E. Are the charge per unit of photosynthesis stimulated by the atomic number 6 drop down strength of rhizobial and arbuscular mycorrhizal symbioses. Soil Biol. Biochem. 41, 1233–1244 (2009).

    CAS  Article  Google Scholarly person

  45. 45.

    Hoagland, D. R. & Arnon, D. I. The water-culture method for growing plants without soil. Univ. Calif. Agric. Reticuloendothelial system. Stn. Circ. 347, 1–39 (1950).

    Google Assimilator

  46. 46.

    Anne Bradstreet, R. B. The kjeldahl method of organic nitrogen. Orifice. Chem. 26, 185–187 (1965).

    Clause  Google Assimilator

  47. 47.

    Li, Z. G., Luo, Y. M. & Teng, Y. Research Methods of Soil and Biology Microorganisms 64–83 (Science Press, 2008).

    Google Learner

  48. 48.

    Mcgonigle, T. P., Miller, M. H., Evans, D. G., Fairchild, G. L. & Drift, J. A. A new method which gives an objective measurement of settlement of roots by vesicular-arbuscular mycorrhizal Fungi. New Phytol. 115, 495–501 (1990).

    Article  Google Scholar

  49. 49.

    Xie, Z., Song, F., Xu, H., Shao, H. & Song dynast, R. Effects of silicon connected chemical process characteristics of maize (Zea Willie Howard Mays Jr. L.) on alluvial dirt. Sci. World J. 2014, 1–6 (2014).

    Google Scholar

  50. 50.

    Chen, X. L., Cardinal, S. Q., Ren, X. L. & Li, S. X. Effect of atmospheric NH3 and hydroponic root nitrogen levels on chlorophyll fluorescence of corn genotypes with several N utilise efficiencies. Acta Ecol. Blunder. 28, 1026–1032 (2008).

    CAS  Google Scholar

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Acknowledgements

This enquiry was fostered by the Natural Science Base of Jiangsu Province (BK20151098, BK20141064), the Six Talent Peaks Project in Jiangsu Province (Project No. 2014-JZ-005), the National Natural Science Foot of China (Project No. 31370533), and the Intoxicated-Level Talent Jut of Jinling Institute of Technology (jit-b-202037).

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X.-M.Z. planned and fashioned the explore, analyzed data, and wrote the manuscript. J.-J.F. performed experiments and revised the manuscript. Z.-P.H. performed information analysis and paper editing. X.-M.L. and W.-X.Z. reviewed the manuscript. All authors read and approved the final manuscript.

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Correspondence to Xue-Ming Zai or Xing-Piece Liu.

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Zai, XM., Fan, JJ., Hao, ZP. et aluminum. Effect of co-inoculation with arbuscular mycorrhizal fungi and phosphate solubilizing fungi along nutrient uptake and photosynthesis of beach medal under salt stress environment. Sci Rep 11, 5761 (2021). https://doi.org/10.1038/s41598-021-84284-9

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