Malick Ndiaye
Alain Mollier
Adama Diouf1,3- 1Laboratoire de Biotechnologies des Champignons, Département de Biologie Végétale, Université Cheikh Anta Diop, Dakar, Senegal
- 2UMR 1391 Interactions Sol Plant Atmosphère (ISPA), Institut National de Recherches pour l’Agriculture, l’Alimentation et l’Environnement (INRAE), Bordeaux Sciences Agro, Bordeaux, France
- 3Laboratoire Commun de Microbiologie, Institut de Recherche pour Développement (IRD)/Institut Sénégalais de Recherches Agricoles (ISRA)/ Université Cheikh Anta Diop de Dakar (UCAD), Centre de recherche de Bel Air, Dakar, Senegal
- 4Polytech Diamniadio, Département Sciences et Techniques Agricoles, Alimentaires et Nutritionnelles, Université Amadou Mahtar Mbow, Dakar, Senegal
Introduction: Soil fertility is a major constraint to agricultural development in the Sahel region of Africa. One alternative to reducing the use of mineral fertilizers is to partially replace them with microbes that promote nutrition and growth, such as arbuscular mycorrhizal fungi (AMF). Mineral fertilizer microdosing is a technique developed to enhance fertilizer efficiency and encourage smallholder farmers to adopt higher mineral fertilizer applications.
Methods: A pot experiment was set up to study the effects of AMF inoculation on the mineral nutrition of pearl millet under mineral fertilizer microdosing conditions. The experimental setup followed a randomized complete block design with five replicates. The treatments tested on millet were an absolute control and eight microdoses derived from the combination of three doses of 15- 10-10 [nitrogen, phosphorus, and potassium (NPK)] mineral fertilizer (2 g, 3 g, and 5 g per pot), three doses of urea (1 g, 2 g, and 3 g per pot), and three doses of organic manure (OM) (200 g, 400 g, and 600 g), combined with and without AMF (Rhizophagus irregularis and Rhizophagus aggregatum). The parameters studied were growth, root colonization by AMF, and mineral nutrition. Plant height, stem diameter, root dry biomass, and percentage of root mycorrhization were measured.
Results and discussion: The results revealed a significant effect of the fertilizers on the growth of pearl millet compared to the control. AMF and OM treatments resulted in the highest biomass production. AMF combined with microdoses of NPK improved N and calcium (Ca) concentrations, while their combination with organic matter mainly improved the K concentration. Combining AMF with microdosed NPK and compost enhanced zinc (Zn) and nickel (Ni) concentrations. Root colonization varied from 0.55 to 56.4%. This investigation highlights the positive effects of AMF inoculation on nutrient uptake efficiency when combined with microdosing fertilization.
1 Introduction
Pearl millet plays an important role in the lives of smallholder farmers in West Africa, serving as a staple food, grain, animal feed, fuel, and construction material (Pucher et al., 2014; Passot et al., 2016; Ndour et al., 2021). It is highly adapted to hot climates with low annual rainfall (300–500 mm) and poor sandy soils, thriving where other crops fail (Supriya et al., 2011; Vadez et al., 2012; Prasad et al., 2017; Ullah, 2017; Faiz et al., 2022). Its production is important for providing significant calorie intake (Serba and Yadav, 2016; Djanaguiraman et al., 2018; Debieu et al., 2018; Diatta et al., 2020).
Despite its significance, pearl millet yields in farming environments remain low, averaging less than 1000 kg ha−1 (Faye et al., 2023). The main constraints to increasing millet production in Senegal include climate change factors such as erratic rainfall patterns, high temperatures, and low soil fertility (Haussmann et al., 2007; Affholder et al., 2013; Defrance et al., 2020; Monerie et al., 2020; Stewart et al., 2020). Additionally, the reliance on rain-fed agriculture, and economic constraints faced by smallholder farmers who have limited incentives to purchase mineral fertilizers, exacerbate production uncertainty and food insecurity (Ganyo et al., 2019; Tounkara et al., 2020; Bastos et al., 2022). Further, the inappropriate use of mineral fertilizers has also led to reduced yields and declining soil fertility (Simpson et al., 2011; Ibrahim et al., 2015). Excess chemical fertilizers can accumulate in the soil (Selim, 2020; Pan et al., 2021), causing soil toxicity, deteriorating soil quality, depleting beneficial soil microflora, and leading to the leaching of toxic elements into groundwater and runoff into water resources (Chaudhary et al., 2017; Meena et al., 2020; Schaefer et al., 2021; Shanmugavel et al., 2023). To improve the efficient use of the mineral fertilizer, the microdosing technology developed by the International Crops Research Institute for the Semi-Arid Tropics (ICRISAT) has shown promising results in enhancing millet yields in the Sahel region of Africa (Aune and Bationo, 2008; Ibrahim et al., 2015; Blessing et al., 2017; Saba et al., 2017; Manssour et al., 2020). This technology involves applying a small amount of mineral fertilizer to the crop seeds at sowing or a few weeks after planting (Aune and Bationo, 2008; Twomlow et al., 2010; Saba et al., 2017). Nevertheless, the low soil organic matter in Sahelian sandy soils limits the effectiveness of this approach (Ibrahim et al., 2015). Therefore, to enhance crop response to fertilizer microdosing, it is essential to combine this method with the application of organic matter (Twomlow et al., 2010).
However, in the context of sustainable agriculture aimed at reducing the use of chemical fertilizers, agricultural productivity increasingly relies on the interactions between soil and microbiota (Thirkell et al., 2017; Genre et al., 2020; Ndour et al., 2021; Adoko et al., 2022). The use of microbial biostimulants in agriculture represents a natural and environmental friendly alternative for enhancing productivity (Fasusi et al., 2021). Several studies have demonstrated the huge potential of plant-associated microorganisms to improve plant nutrition and yield particularly under greenhouse conditions (Pellegrino et al., 2015; Schütz et al., 2018; Syed Ab Rahman et al., 2018; Zhang et al., 2019; Compant et al., 2019). One effective strategy for boosting plant growth and mineral nutrition is to inoculate plants with arbuscular mycorrhizal fungi (AMF). These fungi are integral components of soil and plant roots forming a symbiosis with many cereal crops (Smith and Smith, 2011). AMF enhance plant nutrient acquisition, especially phosphorus (P), in low P soils, by utilizing a symbiotic Pi uptake pathway (Bucher, 2007). This symbiosis improves P uptake efficiency, reducing the need for chemical fertilizers and mitigating potential environmental losses (Adesemoye et al., 2008; Alori and Babalola, 2018; Ghobadi et al., 2020; Trejo et al., 2021; Schaefer et al., 2021). Therefore, understanding the interactions between microbes, fertilizers, and plants is crucial for optimizing these practices (Adesemoye and Kloepper, 2009; Wang et al., 2017; Suman et al., 2022). Several studies have highlighted the benefits of double inoculation with AMF and nitrogen, phosphorus, and potassium (NPK) for plant growth (Adesemoye and Kloepper, 2009; Tshibangu Kazadi et al., 2020; Ziane et al., 2021; Fall et al., 2023; Mulyadi and Jiang, 2023). However, the effects of double inoculation with AMF and fertilizer microdosing on pearl millet in Senegal have not been explored. This study aims to examine the interactions between double AMF inoculation and NPK fertilizer application on nutrient absorption and biomass production in pearl millet. We hypothesize that combining AMF inoculation with NPK microdosing will enhance the plant’s mineral nutrient status and biomass. This study, therefore, sets out to identify optimal microdosing rates for pearl millet in combination with AMF.
2 Materials and methods
2.1 Soil
The experiment was carried out at the Department of Plant Biology, Cheikh Anta Diop University, Senegal. The soil used in this study was collected at the end of the rainy season from Touba Toul at 5–20 cm depth (70 km from Dakar, Senegal). Soil characteristics are detailed in Table 1. The average nutrient content of cow manure, measured at 12% moisture, was 2.28% potassium, 18.64% total carbon, 0.96% total nitrogen, and 0.29% total phosphorus.
Table 1. Physico-chemical properties of soil.
2.2 Mycorrhizal inoculum
Mycorrhizal inocula containing indigenous species (Rhizophagus irregularis and Rhizophagus aggregatum) were obtained from the Laboratory of Fungal Biotechnology (LBC) of the Department of Plant Biology, Cheikh Anta Diop University, Senegal, and multiplied using maize as the host plant. The AMF inoculants used in the experiment were prepared by inoculating sandy soils with spores of Rhizophagus irregularis and Rhizophagus aggregatum separately along with extraradical mycelium generated in pot cultures by maize plants. Spores had an average density of 40 spores per gram of soil per pot. The final inoculum applied was a mixture of both species in equal proportions, resulting in an average density of 80 spores per gram and 85% root infection.
2.3 Experimental design and growth conditions
Traditional pearl millet variety Souna 3 was selected due to its widespread adaptation and preference among smallholder farmers in Senegal (Bastos et al., 2022). The seeds were sown in pots, each containing 3 kg of sandy soil (Table 1), in January. The millet plants were inoculated, and organic matter was added at the time of sowing. One week after germination, the plants were thinned to two per hill. A factorial complete randomized design was used, with treatments including fertilizer with or without AMF inoculum, and five replicates (Table 2). The average nutrient content of cow manure, at 12% moisture, was 2.28% potassium, 18.64% total carbon, 0.96% total nitrogen, and 0.29% total phosphorus. NPK (15-10-10) was applied 10 days after emergence, followed by urea (U, 46% N) 1 month later. The microdosing rates were 0, 0.2, 0.4, 0.6, and 0.8 g per pot, corresponding to 0, 5, 10, 15, and 20 kg ha−1. Plants were inoculated with AMF by adding 20 g of inoculum directly to the roots, while the control received 20 g of sterile soil. The seedlings were grown from January to March in a greenhouse with an average day/night cycle of 12/12 hours, temperatures of 32/25°C, and 40-50% air humidity. Plants were watered with tap water and harvested after 3 months.
Table 2. List of treatments.
2.4 Measurements and chemical analysis
The height and stem diameter of the plants were measured using a graduated ruler and caliper. Twelve weeks after sowing, shoots and roots were harvested separately. Fresh root subsamples were taken to assess root colonization rates. Roots were initially rinsed with tap water and then thoroughly washed with distilled water. The percentage of mycorrhizal root infection was determined by microscopic observation of fungal colonization after clearing the washed roots in 10% KOH and staining with 0.05% trypan blue in lactophenol (v/v), following the method described by Phillips and Hayman (1970). Relative arbuscular richness (i.e., the percentage of arbuscules among AMF structures in the roots) was calculated using the grid-line intersect method (Giovannetti and Mosse, 1980). Root and shoot dry weights were measured after oven-drying at 55°C for 96 hours. Plant analyses were conducted at the UMR Interaction Soil Plant Atmosphere (ISPA) of the National Research Institute for Agriculture, Food and the Environment (INRAE) in France. The dried shoots were ground, and foliar nutrient contents were assessed after digestion with nitric acid (HNO3) + hydrogen peroxide (H2O2). Elements were determined using Inductively Coupled Plasma (ICP). A 500 mg sample of dried powder was mixed with 5 mL of an HNO3/H2O2 mix (4:1, v/v) in a 50 mL Teflon ® tube and placed in a graphite digestion block (DigiPREP MS, SCP Science). The samples were then filtered, and the total concentrations of P, K, calcium (Ca), magnesium (Mg), zinc (Zn), copper (Cu), manganese (Mn), itron (Fe), and nickel (Ni) in the plant digests were measured by inductively coupled plasma atomic emission spectroscopy (ICP-OES) (ICAP 6300, Thermo Fischer). The nitrogen concentration in leaf samples was analyzed using Dynamic Flash Combustion technology (Thermo Flash, EA 1112).
2.5 Statistical analysis
Statistical procedures were conducted using R software version 3.4.4. Data were first tested for normality and homogeneity using the Shapiro-Wilk test. One-way or two-way analysis of variance (ANOVA) was performed to partition the variance into the main effects and interactions between inoculation and fertilization. Significantly different means were identified using the Tukey’s Honestly Significant Difference (HSD) test at a 5% probability level. Results are presented with p < 0.05 considered significant.
3 Results
3.1 Effects of treatments on growth parameters
The treatments significantly affected growth parameters (Table 3). The control treatment exhibited the lowest growth parameters, while the highest growth was observed with the AMF treatment. The tallest plants were recorded with the AMF treatment (107 cm) and OM600 treatment (102 cm), whereas the control had the shortest plants. No significant differences were found among the following combined treatments: (NPK)3U2+AMF; OM600+AMF; OM200+AMF; (NPK)3U2+OM400+AMF and (NPK)5U4+OM600+AMF. Variations in shoot dry weight followed the same trends as plant height.
Table 3. Effect of AMF–NPK fertilizer combinations on plant height (cm), stem diameter (mm), panicle length (cm), dry weight (g), and root AMF colonization in pearl millet.
For stem diameter, analysis of variance and the Tukey test at the 5% threshold identified four distinct groups. The control treatment had the smallest diameter (2.75 mm). The second group included (NPK)3U2 (5.50 mm) and (NPK)5U4 + OM600 + AMF (5.34 mm). The third group comprised treatments combining NPK, urea, AMF, or organic matter (e.g., (NPK)3U2 + AMF; OM600 + AMF; (NPK)2U1 + OM200 + AMF and (NPK)3U2 + OM400 + AMF), with no significant differences among these treatments. The fourth group, with the largest diameters, included the OM600 treatment (9.83 mm) and the AMF treatment (8.88 mm).
Panicle length varied significantly with the fertilization method (Table 3). The control treatment recorded the shortest panicle length (5.10 cm), while the longest panicle lengths were observed with AMF treatment (25.2 cm), OM600+AMF (22.5 cm), (NPK)2U1+OM200+AMF (23.4 cm), and (NPK)5U4+OM600+AMF (21 cm). No significant differences in panicle length were found among these treatments, but significant differences were noted between these treatments and the control.
The colonization of plant roots by indigenous mycorrhizae was influenced by the inoculum (Table 3). All treatments, except the control and OM600 treatments, revealed the presence of infectious units. The highest AMF colonization was observed in the AMF treatment (56.43%). In combined treatments, AMF colonization ranged from 1.6% to 4.2%, with the lowest colonization observed in the (NPK)3U2 treatment.
3.2 Foliar nutrient concentrations
Macro-element concentrations in the shoots of the seedlings after harvest are shown in Table 4. The concentrations of N, P, K, Ca, and Mg in pearl millet shoots were influenced by the different treatments. The (NPK)3U2 + AMF treatment resulted in the highest N concentration compared to other treatments. Analysis revealed the significant contributions of compost, AMF, and microdosed mineral fertilizers to N, P, K, Ca, and Mg concentrations. The highest foliar P concentration was observed in the OM600 treatment, while P concentrations in other treatments did not differ significantly from the control. The most notable differences among fertilized plants were observed in foliar K concentrations. The OM600+AMF treatment had significantly higher K concentrations than other treatments. The Ca concentration in inoculated plants decreased significantly compared to other treatments, with the highest Ca concentration found in plants treated with combined microdosed NPK and urea along with AMF. Other treatments did not show significant differences compared to the control. Mg concentrations followed similar trends to Ca, with significant changes only observed in the (NPK)5U4 + OM600 + AMF treatment.
Table 4. Leaf macro-element concentrations of pearl millet seedlings for different treatments.
Micro-element concentrations in the shoots of the seedlings after harvest are presented in Table 5. The concentrations of Zn, Cu, Mn, Fe, and Ni in pearl millet shoots varied according to the applied treatment (Table 5). The highest foliar Zn concentrations were achieved with combined mineral fertilizers, organic matter, and AMF. Other treatments did not show significant changes compared to the control. Cu concentrations decreased significantly with AMF or (NPK)3U2 treatments compared to the control, with no significant differences among other treatments. Mn foliar concentrations were significantly increased by AMF or (NPK)3U2 + AMF treatments, while the lowest Mn concentrations were recorded with the OM+AMF treatment. No significant differences were found among other treatments. For Fe concentration, no significant differences were observed between treatments. The highest Ni concentrations were found in OM600, AMF, (NPK)2U1 + OM200 + AMF, and (NPK)3U2 + OM400 + AMF treatments, with no significant differences among these treatments or compared to the control.
Table 5. Leaf micro-element concentrations of pearl millet seedlings for different treatments.
4 Discussion
The response of pearl millet to low mineral fertilizer application rates is due to the intrinsic fertility of the soil. Plants could directly acquire sufficient nutrients without their AMF partners after chemical fertilization; while plants might rely on AMF to facilitate the transformation of organic matter following organic fertilization (Liu et al., 2020). This study showed that AMF responded differently to chemical and organic fertilization, suggesting that organic fertilization may activate belowground AMF function to maintain soil nutrients and benefit sustainable agriculture.
The highest root mycorrhizal colonization was achieved with the AMF treatment. The low mycorrhizal fungi colonization at the recommended dose of NPK indicates that the over-application of mineral fertilizers in the pot adversely affects the AMF symbionts, thus reducing the AMF and the benefits provided by the symbionts (Smith and Read, 2010). Many previous studies have shown that the excessive application of chemical fertilizers significantly reduces AMF colonization (Bhadalung et al., 2005; Lin et al., 2012), while other studies have found no significant effect (Chen et al., 2014; Qin et al., 2015) or positive effects (Hazard et al., 2013). In this study, the root colonization rate of the fertilization treatments was significantly lower than that of the no fertilization treatment, ranging from 0.55 to 4.23% (Table 3). The root colonization rate was the highest in the AMF treatment and the lowest in the control treatment. It may be that the soil phosphorus level was moderate in the NPK treatment. With the application of the manure treatment or with the combined mineral fertilizer and manure and AMF, there was a possibility that the soil phosphorus levels were too high or too low. Excessive fertilization significantly reduced AMF colonization due to the higher nutrient availability in the soil after the chemical addition (Hack et al., 2019; Zhang et al., 2021). According to Liu et al. (2020) and Westphal et al. (2008), after the application of the chemical fertilizers, the plant can directly absorb enough nutrients to reduce its dependence on AMF symbiosis. The plant reduces the allocation of photosynthates and reduces the AMF colonization after the application of chemical fertilizers (Trejo et al., 2021).
The performance of AMF combined with different doses of microdosed fertilizers led to significant changes in plant growth parameters. The positive effect of mineral fertilizer was obtained with (NPK)3U2 treatment compared to the control. Plant development and growth conditions were improved by organo-mineral fertilization. This stimulation of growth and development could be linked to a more satisfactory mineral nutrition of the millet with the addition of fertilizer. The positive effect of organo-mineral fertilization on millet development and yield has been reported in the literature (Ndiaye et al., 2019; Pale et al., 2021). Moreover, this effect is more pronounced with the combination of microdosed fertilizer and AMF [(NPK)3U2 + AMF]. Reducing the use of microdosed fertilizer combined with AMF improved growth parameters. This result is significant considering that the improvement in growth parameters was achieved by significantly reducing fertilization. It also helps to demonstrate the environmental benefits of using AMF to improve plant millet growth. The highest growth parameters were obtained with AMF or OM600 treatments. These observations confirm that OM is also a suitable product for soil fertilization. Some previous studies reported an additive effect when combining FM with OM (Bielders and Gérard, 2015; Ibrahim et al., 2015; Somda et al., 2017; Tovihoudji et al., 2019). In contrast, other previous studies have shown that negative interactions between organic amendments and fertilizers are most often observed (Chivenge et al., 2011; Ouedraogo et al., 2021). Indeed, several studies have shown that nutrients from organic matter sources such as crop residues, compost and manure can stimulate mycorrhization (Panja and Chaudhuri, 2004; Gosling et al., 2006; Jan et al., 2014). However, a comparative study of the results obtained with the addition of organic matter combined with AMF (OM600 + AMF) or without AMF showed that the AMF had no effect on millet growth. These results can be explained by the fact that the soil fertility provided by the manure reduced the mycorrhizal potential by affecting AMF development. These results are corroborated by those of Gosling et al. (2006), who states that the effect of organic amendments on mycorrhization is unpredictable because amendments with a high phosphorus concentration can lead to a decrease in mycorrhizal abundance.
The impact of the microdosing fertilizer applied to millet was tested with fertilizer doses respectively lower, equal, or higher than recommended, combined with AMF and manure. The results show that higher fertilizer doses reduce growth parameters. Furthermore, the combination of organic and mineral fertilization in microdosing, which is not favorable for AMF, likely explains the low root infection levels. This suggests that microdosing with both types of fertilizers may not benefit AMF. These results corroborate those of Ricardos et al. (2020), who obtained a greenhouse mycorrhization frequency of less than 45% in maize (Zea mays L.). They explained this low mycorrhization by the low oxygen concentration around the roots confined in the pots.
Nutrients are the determining factors for pearl millet growth and productivity under Sahelian conditions. In this study, AMF and amendment treatments were the most efficient fertilizers in terms of growth parameters under greenhouse conditions. Compost amendment significantly increased the growth parameters. Other researchers have shown a significant effect of compost and AMF complex on plant growth in a greenhouse experiment, where the root colonization and root dry weight were improved (Akhter et al., 2015). AMF and compost have been used to improve the plant growth and mineral nutrition of many species (Mrabet et al., 2014), where a full and different dose of compost inoculated with AMF significantly increased root and shoot biomass (Jan et al., 2014). The use of compost and AMF has also increased growth parameters (Shah et al., 2022). In our study, we assessed for the first time the effect of AMF and microdosing of fertilizer and compost under greenhouse conditions. Small-seeded cereals such as pearl millet require early nutrient supply as the plants will exhaust the seed reserves of nutrients 8–10 days after sowing and all flower parts are formed 30 days after sowing (Rebafka et al., 1993). However, it is well established that nitrogen and phosphorus are the most limiting nutrients in most agricultural soils in sub-Saharan Africa (Kurwakumire et al., 2014; Stewart et al., 2020). Our results demonstrated the efficiency of this combination in increasing mineral nutrition. Leaf mineral nutrition, especially macroelements, efficiently enhanced the effectiveness of microdosing with combined AMF and compost on plant growth. Muchow and Davis (1988) reported that high NPK rates stimulated pearl millet leaf growth, resulting in higher nutrient uptake. Nitrogen and phosphorus uptake was consistently higher. As a result, pearl millet dry matter production and hence nutrient uptake were significantly reduced. The NPK+AMF recommended rate was likely to have taken up more nitrogen and phosphorus than the NPK microdose due to higher nitrogen and phosphorus concentrations. Microdosing of fertilizer increased the branching of pearl millet fibrous root systems, which increased water uptake. This also improved nutrient availability which increased nutrient uptake by pearl millet and thus increased growth and biomass accumulation. Ibrahim et al. (2015) observed that pearl millet crops that received nitrogen and phosphorus at optimal rates were able to grow at their maximum potential, thus increasing N and P uptake. The same conclusion was also reached by Bationo et al. (2005). In contrast, AMF increased the uptake of microelements such as Mn and Ni compared to the control plants. The mixture of microdosed fertilizer and AMF contributed to the uptake of another microelement, Mn. However, the low root colonization in the substrate supplemented with compost compared to the AMF strain alone could be explained by the high availability of macro and micro-nutrients added to the soil via the compost. In particular, the phosphorus may have reduced root colonization. This result confirmed the negative correlation found between the amount of phosphorus and the colonization rate of millet (Bouamri et al., 2006). In addition, the colonization level depended on the composition and maturity of the compost, such as that found in a Zea mays culture (Cozzolino et al., 2016), where compost of 60 and 120 days of maturity negatively affected plant growth and root colonization in greenhouse conditions. Macro and micronutrient concentrations could partly depend not only on the fungal partner but also on the host plant (Ravnskov and Jakobsen, 1995). The most common and well-known interaction of P with micronutrients is the interaction of P with Zn, which can lead to reduction of the concentration of Zn in plants under conditions of excessive P (Barben et al., 2010). AMF and compost have been used to improve the plant growth and mineral nutrition of many species (Mrabet et al., 2014). The combination of compost and mineral fertilizer and AMF seems to favor Zn and Ni over Cu, Fe, and Mn.
5 Conclusion
Microdosing reduced the amount of mineral fertilizer used, improved growth parameters, and increased fertilizer efficiency. However, this practice seems to reduce the mycorrhizal potential by affecting the development of vesicular and arbuscular mycorrhizal fungi. The results of the present study showed that millet production could be further improved by combining inorganic fertilizers with manure application. The highest growth parameters were obtained with combined application of organic matter and NPK. N and Ca concentrations can be improved by using AMF and microdosing NPK, while their combination with organic matter mainly improved K concentration.
Data availability statement
The original contributions presented in the study are included in the article/supplementary material, further inquiries can be directed to the corresponding author/s.
Author contributions
MN: Writing – original draft, Writing – review & editing. AM: Writing – original draft, Writing – review & editing. AD: Writing – original draft, Writing – review & editing. TD: Writing – review & editing.
Funding
The author(s) declare that financial support was received for the research, authorship, and/or publication of this article. This study was funded by the consortium Research Center for International Development (CRDI)/Ministry of Higher Education, Research and Innovation (MESRI) from Senegal (Program SGCI2), grant number: 0002003. And Fellowship Programme French cooperation grants for high-level scientific stays in France (post-doc research internships) program, grant number: 140283W.
Acknowledgments
The authors would like to thank Sylvie BUSSIERE and Catherine LAMBROT (INRAE) for their technical assistance.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
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Keywords: arbuscular mycorrhizal fungi, pearl millet, mineral nutrient, microdosing fertilizer, manure
Citation: Ndiaye M, Mollier A, Diouf A and Diop TA (2024) Mycorrhizal inoculation and fertilizer microdosing interactions in pearl millet (Pennisetum glaucum) under greenhouse conditions. Front. Fungal Biol. 5:1448156. doi: 10.3389/ffunb.2024.1448156
Received: 12 June 2024; Accepted: 01 August 2024;
Published: 29 August 2024.
Edited by:
Syed Riyaz-ul-Hassan, Indian Institute of Integrative Medicine (CSIR), IndiaReviewed by:
Debdulal Banerjee, Vidyasagar University, IndiaXianan Xie, South China Agricultural University, China
Copyright © 2024 Ndiaye, Mollier, Diouf and Diop. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Malick Ndiaye, malick54.ndiaye@ucad.edu.sn