1. Introduction
Nowadays, the deleterious effects of climate change on agricultural systems, coupled with the escalating global population, are anticipated to elevate global hunger by 30% by the year 2050 [
1]. Considering this complex scenario, agriculture has to face the dual challenge of fulfilling the escalating demand for food production while concurrently alleviating its environmental impact on natural ecosystems and human health [
2]. Currently, a spectrum of both traditional and innovative eco-friendly management practices is being widely implemented to augment crop yields and increase food safety standards [
3].
Horticulture, and especially vegetable production, heavily depends on external inputs of mineral nutrients, primarily in the form of synthetic fertilizers. The relatively low nutrient use efficiency exhibited by many vegetable crops leads to an excess application of nutrients beyond what the crops actually require, thereby causing substantial environmental impacts [
4,
5]. This excess application not only raises concerns about resource sustainability but also contributes to environmental issues such as nutrient runoff, soil degradation and water pollution [
6]. Addressing the nutrient use efficiency in vegetable production is crucial for mitigating these environmental challenges and promoting sustainable agricultural practices. Recognizing these concerns, the European Commission has set an ambitious goal to substitute 30% of synthetic fertilizers with greener alternatives by 2050 [
7]. Plant biostimulants, acknowledged as natural products, have emerged as eco-friendly tools for the reduction of synthetic fertilizer use, as they can enhance nutrient use efficiency [
8]. Their application not only contribute in reducing reliance on chemical fertilizers but also helps plants cope with stress induced by climate change [
9,
10]. Therefore, plant biostimulants hold the promise of fostering a more sustainable agriculture, ensuring crop yields under lower inputs, and represent a crucial step towards environmental responsibility [
8,
11,
12,
13,
14].
Non-pathogenic soil microorganisms with beneficial effects on plant growth and crop production can be used as microbial biostimulants in commercial crops [
15]. Bacterial strains living in the rhizosphere or even within the root tissues with beneficial effects on plant growth are generally termed “plant growth promoting rhizobacteria” (PGPR). Due to their beneficial effects on crop yield, several PGPR have been licensed for commercial distribution as biostimulants [
16]. PGPR are usually applied either by inoculating the seeds before sowing or by soil drenching after planting or plant emergence.
The treatment of seeds with microbial preparations is based on specific techniques, which may have different effectiveness–success in coating the seeds, depending on the size, weight, and texture of each seed. Biopriming is a seed-presoaking technique along with the inoculation of beneficial microorganisms. It combines both the biological agent (microorganisms) and physiological soaking (seed hydration) phase [
17]. The exudates released from the seed may serve as source of energy and nutrients to the biocontrol agents during biopriming [
18], thus facilitating the proliferation and the colonization of these biocontrol agents over the surface of seeds which facilitate the nutrient/water uptake. Film coating seed treatment is based on seed coating with a thin film, which contains the active substance-microorganisms and one or two inert materials that function either as a carrier to preserve the microorganisms and/or as adhesives. This film is created after treating the seeds with a liquid-dense solution or suspension [
19].
Zucchini squash (
Cucurbita pepo L.), a member of the Cucurbitaceae family, is a popular vegetable worldwide [
20] of great economic importance due to its high nutritional value [
21]. Zucchini squash is widely cultivated both in fields and in greenhouses in the Mediterranean region [
22] and in arid climatic zones characterized by limited water resources and hot weather conditions as well as in soils with low organic matter content [
23].
Taking the above into consideration, an investigation was designed to assess the effectiveness of a novel inoculant contained the six Bacillus sp. strains in improving nutrient uptake and concomitantly plant growth and yield when used as a PGPR biostimulant through biopriming of zucchini squash seeds.
4. Discussion
In the current study, the inoculation of zucchini squash seeds with the novel mix of
Bacillus sp. strains improved substantially both the vegetative growth and the fruit production of the plants. These results clearly show that this mix of
Bacillus strains includes plant growth promoting rhizobacteria (PGPR) and thus it could be used as a microbial biostimulant. Soil microorganisms have an active role in natural processes that affect soil fertility and soil quality, such as atmospheric nitrogen fixation, organic matter decomposition and mineral nutrition [
26]. These processes are intimately associated not only with the growth and yield of cultivated plants but also with the quality of the obtained products [
27]. Several studies have shown that the use of beneficial rhizobacteria (PGPR) as root inoculants in vegetables promotes plant growth, while it can improve soil composition or resistance to pests and diseases. Therefore, many PGPR strains of mixtures of them are used as commercial biostimulants in agriculture and horticulture. According to the European Council Regulation (2019/1009), biostimulants are defined as plant substances, mixtures, and products of microorganisms, which “stimulate plant nutrition processes independently of the nutrient content in the product with the sole aim of improving one or more of the following characteristics of the plant or the plant rhizosphere: i) nutrient use efficiency, ii) tolerance to abiotic stress, iii) quality traits, or iv) availability of confined nutrients in the soil or rhizosphere” [
28]. The PGPR can be classified into the following two main categories: extracellular root-forming bacteria (ePGPR) and intracellular root-forming bacteria (iPGPR) [
29]. ePGPR live in the rhizosphere or in the spaces between the cells of the root cortex, whereas iPGPR live mainly within specialized nodal structures of the root cells. Also due to their ability to bind to soil nutrients, they improve the levels of nutrients involved in plant cellular processes [
30]. Furthermore, some PGPR strains promote the development of disease suppressants or produce phytohormones that increase plant tolerance to biotic stress thereby acting as biostimulants [
31].
The tested
Bacillus sp. strains mix used as a microbial biostimulant in the current study effectively colonized the zucchini roots, as
Bacillus sp. were present at substantially higher populations in the roots of inoculated plants at the end of the experiment, compared to the non-inoculated plants. Patakioutas et al. [
32] has reported a significant reduction of the population density for
Bacillus amyloliquefaciens when it was used as biostimulant in a soilless tomato crop in a greenhouse. In the current study, the population density was also lower than the initial inoculant and this result indicates that repeated PGPR applications by drenching during the cropping period could potentially increase their effectiveness in terms of crop productivity.
The tested mix of
Bacillus sp. strains improved specifically the uptake of P and its transport to the aboveground shoots, as indicated by the higher leaf P levels in plants from seeds inoculated with the tested PGPR mix. Phosphorus is an essential macronutrient for plants but its availability to plants is marginal in most soils [
33,
34]. Although total P is abundant in the soil [
35], its concentration in the soil solution is mostly lower than 0.1 mg L
−1 (i.e., 0.1 ppm) because of the poor solubility of the phosphoric salts occurring in the soil, which are mostly complexes of calcium phosphates and magnesium phosphates [
36]. As a result, the water-soluble P is quickly depleted in the rhizosphere, and this causes a concentration gradient between the rhizosphere and the bulk of the soil. This gradient contributes to a continuous diffusion of P from the bulk of the soil to the root surface. However, due to the low soluble P concentration in the soil solution, the contribution of diffusion to delivery of P to the root hairs can hardly cover the plant needs, thereby constituting a bottleneck in plant nutrient status [
37]. More specifically, as has been reported by Olsen and Watanabe [
38], the diffusion coefficient for soil P is relatively low, especially when the P concentrations in the soil solution are less than 0.2 mg kg
−1 [
38]. Mass flow also contributes to transport of P from the soil bulk to the surface of the root hairs. However, due to the low P concentration in the soil solution the transport of this macronutrient to the root surface through mass flow is negligible. Indeed, zucchini plants generally require from 0,6 to 1,6 L of water per day [
39]. Thus, even with a P concentration of 1 mg L
−1 in the soil solution, the P delivery via mass flow cannot exceed 1.6 mg day
−1, which is far below the actual plant needs.
Given these limitations in P delivery from the bulk of the soil to the root surface through natural processes, plants have evolved other P transport pathways beyond mass flow and diffusion to fully cover their P needs. These pathways are mostly associated with beneficial effects of soil microorganisms. The most widely known alternative pathway of P transport from the soil bulk to the plant roots is through the hyphae of beneficial fungi, such as the arbuscular mycorrhizal fungi which form symbiotic relationships with the plant roots [
24]. Furthermore, several studies have concluded that many beneficial microorganisms, including bacteria [
40] and fungi [
24] living in the soil, are capable of solubilizing otherwise insoluble soil P [
41]. Thus, through natural selection, phosphate-solubilizing bacteria and plants have evolved mutual relationships of reciprocal symbiosis [
42]. Soil microorganisms can affect P transformation and thus influence the subsequent transportation efficiency of P [
43]. The above statement was confirmed in the study of Gravel et al. [
44] who reported that inoculation of tomato roots with specific PGPR lead to increased P levels in plants shoots when plants were cultivated on an organic medium, while the same plants had no impact on their leaf P status when they were grown on rockwool. The lack of any positive response of plants grown on rockwool to the PGPR is reasonable, since the P concentrations in the nutrient solutions supplied to rockwool-grown crops is mostly higher than 30 mg L
−1 [
10], i.e., much higher than those occurring in the soil solution. Considering the increased shoot P levels in the plants obtained from seed inoculated with the mix of the 6
Bacillus sp. strains in the current study, compared to those from non-inoculated seed, it is reasonable to conclude that this mix acted as a biostimulant contributing to a higher P availability for the roots of zucchini squash. Nevertheless, the current study did not reveal whether the tested mix of microorganisms increased the P availability to the zucchini squash crop through an increased solubility of soil P or through other mechanisms. Hence, further research is needed to unravel the mechanisms deployed by the microorganisms tested in the current study to increase the soil P availability in soil-grown zucchini crops.
Adequate P levels in zucchini shoots range between 4 and 6 mg g
−1 [
45]. Considering this P range, the shoot P levels measured in non-inoculated plants in the current study are considered marginally low, while seed priming with PGPR shifted the shoot P to levels well within the adequacy range. Hence, plants originating from seed treated with PGPR increased plant growth and fruit production, a result which is in agreement with Batista et al. [
46] and Souza et al. [
47] who concluded that increased P availability and absorption leads to yield increase in zucchini plants.
Regarding N concentration, several studies have found that PGPR can increase the N levels in tomato and zucchini shoots [
10,
48,
49]. However, in the present study, PGPR application did not increase the N levels in plant shoots in both experiments. The lack of any effect of the tested mix of PGPR on plant N status was presumably a result of the adequate N supply to all treatments, which was ensured by using the DSS NUTRISENSE to calculate a balanced fertigation scheme throughout the experiment. Thus, the PGPR tested in the current study could not provide an additional benefit to the plants from inoculated seed. Furthermore, the tested mix of PGPR did not increase the potassium levels in the shoot of plants originating from inoculated seed. In agreement with our results, the potassium status in cultivated vegetable plants is usually not affected by the presence of PGPR in their roots [
10,
44,
50].
Organically cultivated zucchini produced from 1.2 to 1.7 kg of fruit per m
-2 [
51], while plants in soilless production systems can reached up to 3.5-6.0 kg m
−2 [
39]. In the current study the application of PGPR in a conventional zucchini crop resulted in substantially higher yield levels than that reported by Montemurro et al. [
51] in organically cultivated zucchini, but lower than in the soilless zucchini crop. Nevertheless, the yield performance of fruit vegetables is also depending on the duration of the harvesting season, which can vary widely depending on the cropping season, the cropping system, and the local cultivation practices.
The comparison of the two genotypes tested in the current study revealed that the local landrace ‘Kompokolokytho’ produced lower shoot fresh and dry biomass and lower total yield compared to the commercial hybrid under greenhouse conditions. However, under open field conditions, the local landrace, and the hybrid ‘ARO-800′ resulted in similar total yields. A likely explanation for the different responses of the two genotypes is the season of the year, which was winter in the greenhouse crop but summer in the open field crop. Presumably, the local landrace has either a lower adaptability than the commercial hybrid under cold conditions or a higher adaptability to hot summer conditions. The latter is more likely, as ‘Kompokolokytho’ is a native landrace of Greece, a country with a hot summer season, and this landrace is traditionally grown in the open field.
Author Contributions
Conceptualization, D.S. and G.N.; methodology, D.S. and G.N.; software, D.S.; validation, D.S.; formal analysis, D.S. and G.N.; investigation, D.S., D.Y. and G.N.; resources, D.S.; data curation, P.M. and D.Y.; writing—original draft preparation, P.M., D.Y. and P.K.; writing—review and editing, D.S, P.K. and G.N.; visualization, D.S., P.M., D.Y., P.K. and G.N.; supervision, D.S. and G.N.; project administration, D.S. and G.N.; funding acquisition, D.S. All authors have read and agreed to the published version of the manuscript.