1. Introduction
Sweet peppers (
Capsicum annuum L.) possess a remarkable economic value for their flavor and distinctive taste [
1]. They are also appreciated due to their antioxidant profile, being an important source of vitamins such as C and A, phenolic compounds and carotenoids [
2]. Their cultivation has high environmental and nutritional demands [
3], and they are suitable for being cultivated all year round in plastic greenhouses, especially in Spain and the Mediterranean basin. Consequently, peppers play an important role in the horticultural sector of Spain, since the country is the leading producer of peppers in the EU, particularly concentrated in the southeast [
4].
Intensive farming practices typically involve high inputs of water, fertilizers and pesticides to maximize productivity. However, their excessive use leads to soil and water degradation, which, in combination with the negative effects of climate change, represents an unsustainable farming system in the long term [
5]. As a result, agriculture is gradually shifting toward more environmentally friendly farming systems, which include the use of high-frequency fertigation, biological pest control, and research about the optimization of fertilizers application and the implementation of sustainable strategies, such as plant biostimulants [
4]. In this context, selecting pepper cultivars with a positive response to reduced inputs is crucial, as pepper development is highly sensitive to water and nutrient deficits, which directly affect yield [
6].
Plant biostimulants have emerged as promising tools for sustainable agriculture, both in organic [
7] and conventional systems such as greenhouse cultivation [
8]. According to European Regulation (EU 2019/1009), plant biostimulants are defined as EU fertilizing products that can enhance plant nutrition processes. The aim is to improve one or more of the following aspects of the plant or its rhizosphere: (i) nutrient use efficiency, (ii) tolerance or alleviation to abiotic stresses, (iii) quality traits, and/or (iv) the availability of immobilized nutrients in the soil or the rhizosphere [
9].
Plant biostimulants have been classified into six non-microbial and three microbial categories. Microbial biostimulants involve non-toxigenic, non-pathogenic microorganisms, corresponding to: (i) bacterial plant biostimulants, belonging to genera like
Azospirillum spp.,
Rhizobium spp., or
Azotobacter spp.; (ii) arbuscular mycorrhizal fungi; and (iii)
Trichoderma spp. [
10]. Microbial biostimulants are of particular interest since plants host a diverse and complex array of microorganisms in their endosphere, phyllosphere and rhizosphere. The establishment of symbiotic interactions between plants and microorganisms is a fundamental and prevalent aspect of plants, coevolving with these microbial symbionts, which play important roles in nutrient uptake, plant performance and yield [
11].
Bacterial plant biostimulants can be further subcategorized into plant growth-promoting bacteria, with plant growth-promoting rhizobacteria (PGPR) being the most extensively studied group. PGPR can colonize plant root systems and adhere to the rhizosphere [
12]. These microorganisms are able to enhance plant development through nitrogen fixation, phosphate solubilization, siderophore production and phytohormone synthesis, among other effects [
13]. Their enzymatic activities support soil functioning, serving in parallel as markers of microbial efficiency and soil vitality [
14].
Among the commonly measured enzymatic activities, alkaline phosphomonoesterase (ALP) is involved in organic phosphorus mineralization and it is considered a valuable microbial indicator due to its predominantly microbial origin [
15]. Catalase (CAT), which is present in plants, animals and microorganisms, mitigates oxidative stress by breaking down hydrogen peroxide (H
2O
2) into water and oxygen [
16]. In the rhizosphere, CAT activity also reflects microbial activity, as many soil microorganisms contribute to the degradation of organic matter and the regulation of oxidative stress [
17]. Dehydrogenase (DH) is a marker of microbial respiration, linked to microbial metabolic activity, particularly in redox processes that are essential for maintaining soil fertility. DH activity is also involved in humus decomposition and organic matter [
18].
Hence, the main aim of this work was to assess the impact of reduced fertilization and irrigation on a collection of sweet pepper varieties, as well as the potential effects of applying a commercial PGPR biostimulant. The main agronomic traits (yield and fruit weight) were assessed throughout the reproductive stage of the crop. The effect of treatments at the rhizosphere level was studied through the determination of ALP, CAT and DH enzymatic activities. In addition, given the relevance of sugars to organoleptic fruit quality in sweet peppers [
19], glucose, fructose and sucrose concentrations were quantified in both unripe/green-ripe and fully ripe fruits. The genotype had a significant influence on all evaluated traits. By contrast, the effects of the stress treatments and PGPR inoculation were more limited, particularly regarding agronomic traits. For sugars, the ripening stage also had a significant influence, with some effects observed in specific treatments and a relative enhancement associated with PGPR application, especially at the green-ripe stage. These results provide valuable insights into specific genotype responses under low-input conditions and support the identification of promising candidates for sustainable pepper cultivation.
4. Discussion
Most pepper varieties cultivated in the Mediterranean basin are high-demand cultivars [
27], well-adapted to greenhouse production systems [
4], and optimized for high yields [
28]. However, the urgent need to transition to more sustainable crop management is promoting the optimization of agronomic inputs [
29] and the identification of genotypes better adapted to low-input conditions, which includes local ecotypes [
30]. This shift also reflects the priorities set by the Common Agriculture Policy (CAP 2023–2027) [
31]. In this context, our study evaluated yield and fruit weight, three selected rhizosphere enzymatic activities, and the fruit sugar profile at green-ripe and red maturity stages in seven sweet pepper genotypes. Six treatments were tested, combining two fertilizer and irrigation regimes, with PGPR inoculation. Identifying well-performing genotypes under reduced inputs and in response to PGPR is a key step toward sustainable pepper cultivation [
32].
Yield is a complex trait influenced by environmental conditions as well as genotype-related factors, such as vegetative development, fruit weight and fruit number [
33]. Optimizing input requirements is essential to balance productivity with sustainability [
34]. In our study, fertilizer reduction did not significantly compromise yield or fruit weight, suggesting tolerance to lower nutrient inputs. These data are consistent with Vadillo et al. [
35] for commercial and total yields in green peppers, although other authors reported increased pepper yields with higher nitrogen availability [
36]. By contrast, irrigation reduction in our study produced genotype-dependent responses, with some genotypes maintaining yield, others declining, and even increasing productivity. Significant reductions under water stress were also reported by Çolak et al. [
37] and Mostafa et al. [
38]. Combined stress of reduced fertilization and irrigation further decreased yield and fruit weight in some of our genotypes. This negative effect was supported by Zhang et al. [
39] and Xiang et al. [
40] in different sweet peppers, whereas Zamljen et al. [
41] reported variable responses in pepper yield and fruit dry weight under multiple fertilizer and irrigation combinations. PGPR inoculation has been reported to enhance agronomic traits in pepper seedlings and other crops under stress conditions [
42,
43]. In contrast, PGPR did not increase yield or fruit weight in our study. This finding aligned with authors that reported limited effects of bacterial biostimulants under nutrient or water reduction [
44,
45]. This lack of response may be explained by the restricted adaptability of most PGPR strains, whose efficacy is highly dependent on host genotype, cultivation practices and soil type [
46]. It is also influenced by competition with endogenous microbial communities [
47] and by strains’ ability to adopt survival strategies under water deficit, such as siderophore and microbial exopolysaccharide production [
48], or under reduced fertilization, which may involve nitrogen fixation, linked to the presence of
nifH genes [
49]. Overall, the limited changes observed in yield and fruit weight across treatments in our collection were in agreement with the non-significant G × T interaction for yield, and the low significance of G × T interaction detected for fruit weight, indicating that the differences observed were mostly attributed to the main effects, i. e., genotype and treatment.
In our collection, although the commercial hybrid Cabañeros F1 had the highest yield and fruit weight under control conditions, its performance was declined under stress. In contrast, the experimental hybrid H2 achieved the highest average yield across treatments. In particular, Najerano, Piquillo, H2 and Isabel F1 were the best-performing genotypes under low-input treatments due to their stability, highlighting the potential of traditional cultivars for sustainable farming [
50,
51]. Previous studies suggest that part of this genotype-dependent tolerance to certain abiotic stresses is linked to root architecture [
52] and their specific interactions with soil and microbial communities [
21]. These results are particularly relevant in Mediterranean horticulture, where water scarcity and salinization are major challenges [
53]. They also align with the European Green Deal and the Farm to Fork strategy, which set ambitious targets for reducing fertilizers, among other chemicals, by 2030 in EU Member States [
54].
At the soil level, microorganisms are key endogenous biological components, driving essential biochemical processes [
55]. Plant roots influence soil properties by realizing metabolites into the rhizosphere, stimulating microbial activity, and creating enzyme hotspots that foster plant-microbe interactions [
56]. Among these microorganisms, PGPR are of particular interest because they cannot only promote plant growth, but also improve rhizosphere environment through their influence on biochemical processes and microbial dynamics [
57].
ALP activity differed among our genotypes under fertilizer reduction. High variability in ALP activity has been reported in other studies, with increases in fertilized soils compared to unfertilized ones, sometimes linked to nitrogen availability, which can promote microbial growth and greater enzyme production [
58]. Conversely, other studies observed higher ALP activity in unfertilized plots [
59], possibly due to the inhibition of the
phoD gene by orthophosphate from mineral fertilizers, as
phoD encodes alkaline phosphatase enzyme [
60]. However, some authors found stable ALP levels regardless of fertilization [
61]. Under irrigation reduction, ALP activity tended to decrease due to reduced microbial activity and phosphatase production [
62,
63]. In our study, only a subset of genotypes showed a significant reduction in ALP activity under water deficit, while several genotypes maintained stable ALP levels. This genotype-dependent variation in ALP activity has been documented previously [
64,
65]. Additionally, in our study, PGPR inoculation generally had little effect compared to the corresponding stress treatments, in line with observations reported by Jing et al. [
66]. By contrast, positive effects have been reported in other studies, such as in yellow lupine with
Bacillus subtilis under unfertilized conditions at the emergence stage [
67], and in
Poa pratensis with
Morchella inoculation under drought [
68].
CAT activity remained largely stable in most of our genotypes under reduced fertilization, which was consistent with Yuan et al. [
61]. Other studies observed marked increases in CAT activity with fertilization [
69], reporting that organic fertilizers can produce a higher impact on this enzyme compared to chemical ones, since fertilizer type can influence microbial communities and organic matter dynamics [
70]. Irrigation reduction produced variable responses in our study, since some genotypes increased CAT activity under water deficit, while others experienced a reduction compared to control. Similar contrasting outcomes have been reported in the literature [
65,
71], indicating that CAT activity depends on soil conditions, genotype-specific responses of plant host and shifts in microbial communities [
72]. Again, PGPR inoculation did not generally modify CAT activity in our genotypes compared to their corresponding stress treatments. These results were consistent with observations in PGPR-inoculated poplar seedlings under drought compared to non-inoculated plants under stress [
66]. Conversely, positive effects have been described in other studies, such as in yellow lupin inoculated with
B. subtilis under unfertilized conditions compared to non-inoculated plants under stress [
67].
For DH activity, reduced fertilization did not produce major differences among our genotypes. However, the literature reports variable trends, as some studies observed increases in DH levels under both mineral and organic fertilization [
73], while others reported no significant changes under mineral fertilization but increases with certain organic amendments [
74]. Some studies also indicated reductions at higher mineral fertilizer doses [
75]. Regarding water reduction, DH activity is frequently associated with declines [
76,
77]; however, our findings showed no significant differences under irrigation reduction, remaining stable under stress. Similar results were partially reported by Atika et al. [
78] in some of the evaluated species. Regarding PGPR inoculation, its effect was generally limited in our genotypes. In contrast, variable responses have been reported by authors, such as Sood et al. [
79], who observed variable tendencies in DH values in wheat soil inoculated with PGPR under various reduced fertilization doses. By contrast, Nader et al. [
80] showed that
Bradyrhizobium japonicum enhanced DH activity in soybean under reduced fertilization and under combined drought and low fertilization at the early pod stage, compared to non-inoculated plants at full doses. Similarly, Atika et al., [
78] reported increased DH activity under severe and moderate drought in PGPR-inoculated
Atriplex halimus and
Peganum harmala, respectively, although no effect was detected in
Pennisetum setaceus, compared to non-inoculated plants under the same drought levels.
In general, rhizosphere enzymatic activities showed limited responses to treatments in most genotypes. Only a few genotype-specific patterns, particularly for ALP and CAT, were in agreement with the highly significant G × T interaction reported by the ANOVA. The stability of DH was consistent with its non-significant G × T interaction. This limited response could be attributed to environmental conditions, soil characteristics, or limited microbial interactions within the rhizosphere of our pepper cultivars [
46,
65]. Nevertheless, this consistency under stress conditions suggested a degree of resilience in maintaining soil functionality under low-input farming, which aligned with the stability observed in yield and fruit weight. Notably, BGV13004, H1 and Isabel F1 showed the strongest increases in rhizosphere enzymatic activities under stress or PGPR inoculation, suggesting the establishment of particular relationships with microbial communities at the rhizosphere level [
81], and highlighting their potential for sustainable agriculture.
Free sugars are important contributors to pepper fruit flavor, nutritional value and consumer acceptance [
82]. They also play a key role in plant growth, flowering, and in the responses to different abiotic stresses [
83]. Because sugar concentrations in pepper fruits typically increase during ripening [
84], our analysis were performed separately for green-ripe and fully ripe stages.
The effects of fertilization on sugar accumulation in horticultural crops are complex, and the literature reports no consistent trends [
85]. In our study, sugar concentrations remained mostly stable across genotypes and ripening stages, indicating limited sensitivity to fertilizer reduction. These results agreed with previous studies in ripe peppers, where glucose content was unaffected by varying nitrogen doses [
33]. Similar stability was observed for soluble and reducing sugars under moderate fertilizer reductions, although severe nutrient limitation was associated with declines [
86]. Conversely, Urrea-López et al. [
87] reported a significant increase in fructose under low nitrogen in Habanero pepper. Water reduction is commonly associated with sugar accumulation, since soluble sugars contribute to osmotic potential, maintain cell turgor, and mitigate changes in water potential [
88]. Consistent with this, Haris et al. [
89] observed increases in fructose, glucose, and sucrose contents in peppers under severe irrigation stress. Similar results for fructose and glucose were reported in tomato by Lu et al. [
90]. In contrast, Zamljen et al. [
91] found higher sugar contents under full irrigation in peppers. In our collection, most genotypes showed no significant changes in sugar content, being particularly stable at green-ripe stage. This finding was consistent with the study of Poomkokrak et al. [
92], who reported stable glucose concentration in cherry tomato under water stress. The general stability in sugars between control and reduced irrigation in our study suggested that sugars played only a minor role in the response to water deficit, or that stress intensity was insufficient to induce marked sugar accumulation in fruits. Moreover, the limited impact of water reduction on yield and fruit weight indicated that the observed sugar stability was not merely a consequence of concentration or dilution effects related to fruit weight, as commonly reported in other studies [
93,
94]. PGPR application has been widely explored as a strategy to improve not only crop health and productivity, but also fruit quality [
95]. In our study, PGPR inoculation positively influenced the sugar profiles of certain genotypes at the green-ripe stage, including Piquillo, Najerano, H1 and Isabel F1. This suggests that plant-microbe interactions in the rhizosphere can modulate plant host physiology and metabolites related to fruit composition [
96]. The rest of the collection generally did not show significant effects in the presence of PGPR, as was reported by Del Amor et al. [
97], who observed no significant changes in sugar content in green peppers under low nitrogen with PGPR compared to full fertilization. At the fully ripe stage, PGPR effects were limited. The complex metabolic changes that occur during ripening may partially explain the lack of clearer PGPR effects at full ripeness [
84]. Similar observations were reported by Del Amor et al. [
97], who found no significant differences in glucose and fructose contents between low fertilizer and low fertilizer with PGPR in ripe peppers. Conversely, Kim et al. [
96] reported reduced total soluble sugar content in pumpkin inoculated with
Kushneria konosiri, under drought compared to non-inoculated stressed plants.
Although commercial hybrids generally exhibited higher sugar contents at the green-ripe stage, several traditional genotypes and experimental hybrids displayed interesting sugar profiles at full ripeness, highlighting their potential for breeding programs targeting fruit quality [
27]. These differences in sugar accumulation were reflected in the variable responses to treatments depending on genotype and ripening stage, which corroborates the significant G × R interaction and, to a lesser extent, in some G × T interactions.
Additionally, BGV13004 and H1 improved their sugar profiles under specific stress conditions in green-ripe peppers, while H1 and Isabel F1 showed the highest performance at fully ripe stage. PGPR inoculation enhanced sugar content in Najerano, Piquillo, H1 and Isabel F1 at the green-ripe stage, whereas H2 was the only genotype to benefit from PGPR at full ripeness. Although PGPR did not improve yield or fruit weight in our collection, increases in specific sugars in some genotypes highlight improvements in fruit quality under low-input conditions. Moreover, the effect of PGPR was influenced by genotype and ripening stage, suggesting that these microorganisms can be strategically applied to enhance fruit quality in sustainable agriculture. To improve the identification of PGPR strains with beneficial effects adapted to specific cultivars and environmental conditions, several authors recommend implementing molecular tools. These approaches include the analysis of specific plant stress-related genes responsive to PGPR, as well as broader studies of transcriptional responses of cultivars under stress combined with PGPR [
49,
98].
Identifying genotypes that combine stable yields and rhizosphere enzymatic activities with enhanced sugar contents under stress, alongside complementary strategies such as PGPR inoculation, represents a promising step toward sustainable pepper breeding adapted to the new Mediterranean conditions. Future multi-year and multi-location studies could further validate the broader applicability of these findings on other different pedoclimatic conditions.