Next Article in Journal
Quantifying Root-Soil Interactions in Cover Crop Systems: A Review
Next Article in Special Issue
A Review of Representative Methods Used in Wine Authentication
Previous Article in Journal
German Farmers’ Attitudes on Adopting Autonomous Field Robots: An Empirical Survey
Previous Article in Special Issue
Effects of Development Stage and Sodium Salts on the Antioxidant Properties of White Cabbage Microgreens
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Application of Novel Microorganism-Based Formulations as Alternative to the Use of Iron Chelates in Strawberry Cultivation

1
Department of Agriculture, Food and Environment—University of Catania, Via S. Sofia 98-100, 95123 Catania, Italy
2
Department of Horticulture, “Ion Ionescu de la Brad” University of Agricultural Sciences and Veterinary Medicine, M. Sadoveanu, 700440 Iasi, Romania
3
Department of Agricultural, Environmental and Food Sciences, University of Molise, 86100 Campobasso, Italy
4
“King Michael I of Romania”, Banat’s University of Agricultural Sciences and Veterinary Medicine, 220 Calea Aradului, 300645 Timisoara, Romania
*
Author to whom correspondence should be addressed.
Submission received: 29 January 2021 / Revised: 1 March 2021 / Accepted: 3 March 2021 / Published: 6 March 2021

Abstract

:
The strawberry is a low-growing, herbaceous perennial plant, sensitive to iron deficiency. The iron deficiency represents a nutritional disorder, leading to a decreased content of photosynthetic pigments, which determines the yellow color characteristic of chlorotic leaves. Therefore, in calcareous soils, the use of synthetic iron chelate is often mandatory in strawberry cultivation. The employment of novel microorganism-based formulations as alternatives to the use of iron chelates, was evaluated during strawberry cultivation by monitoring the morpho-biometric parameters, chlorophylls, the iron content in leaves and roots, and the Fe chelate reductase activity involved in absorption of iron during the chlorosis event in plants using the strategy I. The experimental design envisaged growing strawberry seedlings on an inert substrate (pumice), irrigated with Hoagland solution iron-free, with a 12 h photoperiod. After 42 days, at the first appearance of chlorosis symptoms, plants were transplanted into a calcareous soil, and after seven days, they were treated, by a single application, with a microorganism-based formulations (MBF), an inoculum (In) of Trichoderma spp. and Streptomyces spp., or Sequestrene (Sq). Strawberry plants were sampled and analyzed at 5, 10, 15, and 20 days from the treatments. The results showed that microorganism-based formulations positively affected the strawberry seedlings, by reducing the chlorosis symptoms, producing comparable effects to the Sequestrene treatment.

1. Introduction

Iron deficiency is an important nutritional disorder in plants, resulting from the altered acquisition and use of Fe, rather than from a low level of Fe in soils, determining as the primary effect a decreased content of photosynthetic pigments, which leads to the characteristic yellow color of chlorotic leaves [1]. The ferric chlorosis is determined by iron necessity for the correct functionality of proteins involved in the synthesis of chlorophylls. Indeed, the synthesis of δ-aminolevulinic acid, precursor of chlorophylls, is regulated by the presence of iron [2]. Iron is also necessary for the synthesis of the protochlorophyllide from Mg-protoporphyrin. Moreover, in the thylakoid membrane, 20 atoms of iron are needed for photosynthetic electron transport chain of the PSII and PSI photosystems [3,4,5]. Such metabolic disorders induced by Fe deficiency cause chloroplast disorganization. This effect is shown by decreasing of photosynthetic units, granules, and stromal lamellae of the chloroplast, and by the decrease of thylakoids [6].
Different soil factors, including alkaline pH (nearly 8.0), free CaCO3, and HCO3, influence the iron availability for the plants [7]. In fact, in calcareous soils, where free CaCO3 reacts with soil moisture and CO2 leads to the production of HCO3, Fe deficiency represents a crucial factor for crop growing [8,9]. Therefore, iron deficiency is one of the main factors related to the reduction of crop yield in calcareous soils, making the Fe uptake by the plants difficult due to its physical and chemical properties [10,11]. In this context, the microorganisms of the soil have an important role, as mineralizing the organic matter determines the release of iron cations Fe2+ and Fe3+. In the soil, the redox equilibrium is shifted from the reduced form (ferrous iron) (Fe2+) to the oxidized form (ferric iron) (Fe3+), determining the precipitation of cations as ferric hydrates. Iron is absorbed by plants in cationic form, and Fe2+ represents the favorite form [12]. The iron bioavailability in the soil is correlated to a balancing between the ions and free oxides as a consequence of pH and redox potential [13]. Therefore, the iron availability in the soil and rhizosphere depends on its concentration in the soil solution, and on the ability of the solid phase to supply the liquid phase of soluble forms through the balance between processes of solubilization/precipitation and dissociation/formation of the complex, occurring in the soil [13].
The plants have acquired specific absorption systems for iron to cope with its deficiency. The dicotyledonous and monocotyledon not graminaceous plants use a system strategy named “strategy I”, in which the plants secrete in the soil specific organic compounds, such as malic acid and citric acid, together with protons (due to membrane ATPase pumps) [12]. These substances decrease the soil pH and form more stable chelate of the previous iron chelate, allowing them to reduce iron to the Fe2+ form at the cell membrane level. The ability to reduce the Fe(III) to Fe(II) is attributable to the membrane enzyme named Fe chelate reductase, which acts as a NADH-dependent reductase. This result is stimulated by the decrease of pH induced by the activity of protonic pumps [14].
“Strategy II” is active in to graminaceous plants, which secrete chelating organic substances in the soil called phytosiderophores (mugineic acid, avenic acid, etc.). The phytosiderophores have the ability to chelate Fe3+ and carry it inside the cell through the membranes [15].
It has also been shown that humic substances (HS) have an important role in Fe assimilation. In fact, soluble Fe-HS complexes, naturally present in the soil, can promote iron acquisition by providing a readily available iron in the rhizosphere and by directly affecting plant physiology through mechanisms involved in Fe acquisition acting at the transcriptional and post-transcriptional level in the plant [16,17].
Moreover, soil microorganisms, such as a mixture of Trichoderma spp. and Streptomyces spp., are also able to produce siderophores, which are similar to those produced by the plants [18,19]. Siderophores are small and high-affinity iron-chelating compounds that microorganisms synthesize under iron-deficiency stress in order to guarantee the growth and development of their cells by increasing soluble iron in the soil and making it available for themselves [20]. These types of secondary metabolites promote the chelation of iron, making it more available for the microorganisms the produced it, and at same time for the plants [21,22]. Indeed, Zhao et al. [18] found that in Arabidopsis, the siderophores produced by Trichoderma asperellum Q1 in the soil act by enhancing the conversion of poorly soluble Fe. In soil inoculated with Trichoderma asperellum, the soluble Fe and siderophores increased and the growth in cucumber seedlings grown in the inoculated soil were enhanced by increasing the ferric chelate reductase (FCR) activity in roots [23]. Therefore, the siderophores produced by several rhizosphere microorganisms may be very useful for promoting the absorption of iron by plants in an iron-deficient environment [24,25].
Iron deficiency represents a limiting growing factor for those horticultural crops, such as strawberry, requiring highly specialized knowledge and high external inputs [26,27]. Among the chelating agents, the most used for iron complexation is ethylenediamine-N (o, p-hydroxyphenylacetic) acid (EDDHA), and in particular its isomeric “orto” form, which guarantees the highest stability level of the ion. Other iron chelating agents are ethylenediaminetetraacetic acid (EDTA), ethylene diamine di(hydroxy methyl phenyl) acetic acid (EDDHMA), and ethylenediamine di (2-hydroxy-4 carboxyphenyl acetic) acid (EDDCHA). In particular, soil management, irrigation, and fertilizations are all crucial events in order to obtain favorable strawberry productions, although an excess of these compounds often results in environmental problems [27,28]. In addition, chemical compounds may also negatively affect the beneficial soil microorganisms, therefore horticulture is addressing the reduction of the use of these chemical compounds [29,30]. In this respect, FAO [31] suggested that in order to create a safe environment, agriculture must contribute to improving the living standards of all, especially the poorest, in an economically, socially, and environmentally sustainable manner.
The aim of this study was to verify the efficiency of new microorganism-based formulations (MBF and In) against iron deficiency, in order to evaluate the iron absorption efficiency by plants as well as Fe solubility in a calcareous soil. Finally, the efficiency of these commercial formulations was compared to the well-known effect of the iron chelate Sequestrene.

2. Materials and Methods

2.1. Plant Material and Growth Conditions

The trials were conducted using strawberry plants (Fragaria × ananassa Duch. cv. ‘Portola’), with bared roots, at the stage of two true leaves, provided by a local farmer in Maletto (Catania, Sicily, Italy). The seedlings were washed with distilled water, and transplanted into containers (30 × 45 × 20 cm) filled with an inert support (pumice) as substrate, sprinkled with 1 L of nutrient solution of Hoagland iron-deficient solution (5 mM Ca(NO3)2, 5 mM KNO3, 1.0 mM KH2PO4, 2.0 mM MgSO4, 46.0 mM H3BO3, 0.8 mM ZnSO4, 0.4 mM CuSO4, 9.0 mM MnCl2, and 0.02 mM MoO3), in order to induce chlorosis symptoms in strawberry seedlings. In each container, 5 strawberry plants, for a total of 85 seedlings for each of the three repetitions, were transplanted.
The pH of the nutritive solution was 6.4 ± 0.2 and the electrical conductivity (EC) was 2.2 ± 0.2 dS m−1. Hoagland solution was periodically added to keep a constant pH and electrical conductivity in the solution. The experimentation was performed in May, using laboratory conditions in a climatic chamber, with a photoperiod of 12 h of light at room temperature (23–27 °C). SPAD values (SPAD-502 Leaf Chlorophyll Meter, Minolta Camera Co., Ltd., Osaka, Japan) were recorded every 7 days, as described in Barone et al. [32], to monitor the iron deficiency levels. After 42 days, at the first sign of chlorosis symptoms on a new leaf (with total chlorophyll content < 150 µmol m−2), seedlings were transplanted into a plastic pot (diameter 20 cm, height 20 cm) filled with soil and grown for 7 days. After the treatments, plants were grown for a further 20 days.

2.2. Soil Characterization

The substrate used in the experimental trials was a calcareous soil clay-loam (sand: 32%; silt: 30%; clay: 38%). The values of pH, electrical conductivity (EC), organic matter (OM), organic carbon (OC), cation exchange capacity (CEC), total CaCO3, active CaCO3, total iron (in aqua regia), extractable iron (in oxalate), available iron (present in exchange complexes), and readily available iron (present in soil solution) were previously determined (Table 1). The chemical characterization was carried out according to Violante [33] and Barone et al. [34]. Soil was chosen for its chlorosing power index (CPI), calculated as the ratio between active calcareous (mg/kg) and the square of extractable iron (ppm). If the calculated index is greater than 100, soil will potentially determine chlorosis symptoms in the crops [35]. Before transplant, in order to improve some soil physical characteristics (such as porosity and structure), bovine manure (0.5 kg/m2) was added [36].

2.3. Treatments

Seven days after the transplant, the following soil treatments were performed: (I) CNT, control (no treatment); (II) Seq, treatment with Sequestrene at the recommended dose of 2 g/m2; (III) MBF, treatment with microorganism-based formulations at the recommended dose of 2 mL/m2; (IV) In, treatment with inoculum of MBF + molasses, in dose of 2 mL/m2.
As synthetic chelating was used, the Sequestrene® (Syngenta NK 138Fe, Basel, Switzerland) was composed of 3% total nitrogen, 15% K2O, 6% soluble Fe, and 5.5% chelating Fe with EDDHA (3% as [o,o]). MBF consisted of 5% soluble Fe, 2% chelating Fe with EDDHA ([o,o]), and an inoculum composed of: organic matter, 0.0001% Glomus spp., 103 UFC/g rhizosphere bacteria, 108 UFC/g of Trichoderma, and >108 UFC/g Streptomyces spp. and Trichoderma spores. Inoculum (In) consisted of organic matter, 0.0001% Glomus spp., 103 UFC/g rhizosphere bacteria; 108 UFC/g of Trichoderma asperellum, and 108 UFC/g Streptomyces avermitilis and 108 UFC/g Trichoderma asperellum spores.
Soil treatments were performed in only one liquid application at the soil level. MBF was reconstituted by dissolving the inoculum in the nutritive base (according to manufacturer’s instructions, the inoculum was added at 2%), diluted in water (200 mL), and applied at the recommended dose (as previously described).
Inoculation of the soil with microorganism was performed by diluting the inoculum (provided by the manufacturer) in water (the inoculum was added at 2%, in 200 mL), and by applying it directly into the soil.
Plants were treated 7 days after transplanting in the soil. For each thesis and replica, 20 seedlings were treated and monitored for 20 days. Every 5 days, samples from 5 plants for each thesis and replica were harvested and analyzed; consequently, the determination were performed at T5, T10, T15, and T20. T0 consisted of 5 plants harvested and analyzed before the treatments. For each thesis, 3 replicas were performed. During the experimental period seedlings were irrigated with a drip irrigation system.

2.4. Determination of Fresh and Dry Weights, and Chlorophylls

The strawberry seedlings were collected and roots and leaves were separated and weighted. For dry weight determination, plant samples were separately dried at 105 °C, until a constant weight was reached [37].
The chlorophyll content was monitored using the SPAD values (SPAD-502 Leaf Chlorophyll Meter, Minolta Camera Co., Ltd., Osaka, Japan) in accordance with Pestana et al. [38]. The measures were taken 5 times on at least 3 leaves for each plant. The SPAD values were converted into quantitative total chlorophylls (mmoli·m−2) using a calibration curve. The calibration curve was made by analyzing portions of leaves with different degrees of chlorosis, measuring both SPAD values and chlorophyll content by spectrophotometric method of extraction in acetone described by Puglisi et al. [39].

2.5. Iron Content in the Plants

The plant iron content was measured in both leaves and root [40]. The samples were washed with deionized water with 0.01 M HCl solution. The plants were dried until constant weight at 105 °C and subsequently incinerated in a muffle furnace at 500 °C for 24 h. The resulting ashes were dissolved in 10 mL of 1% (v/v) HNO3, filtered with Whatman 0.45 μm filters (Whatman® Schleicher & Schuell, Dassel, Germany), and the Fe content was determined by atomic absorption (Perkin Elmer, Norwalk, CT, USA).

2.6. Ferric Chelate Reductase Activity in Roots

The roots (about 2 cm) were cut; washed with distillated water; immersed in a solution containing 0.5 mM CaSO4, 0.25 mM Fe(III)-EDTA, 0.6 mM bathophenanthroline disulfonate (BPDS), and 10 mM Mes-KOH (pH 6); and kept in the dark for 60 min [40]. The activity was measured by monitoring the increase in absorbance of the solution in contact with the root at 535 nm, due to the root’s capacity to reduce the Fe(III)-EDTA with the production of colored Fe(II) batophenantrolina complex (BPS-Fe2+) [41]. After sample centrifugation, the absorbance was measured by spectrophotometer (Jasco, Tokyo, Japan). The nmoles of BPS-Fe2+ produced were calculated using the molar extinction coefficient equal to 22.14 mM cm−1 [42].

2.7. Statistical Analysis

The data of fresh and dry weights, iron content, chlorophyll content, and Fe chelate reductase activity were analyzed by one-way ANOVA (one way, p < 0.05), followed by a Tukey test.

3. Results

Fresh and dry weights of strawberry seedlings were monitored for 20 days and measured every five days (Figure 1 and Figure 2).
As shown in Figure 1A, the leaf fresh weight after 5 days (T5) from the treatment significantly increased (about 88% than the control) only in strawberries that were treated with Sequestrene (Seq). After 10 days (T10) from the treatment, seedlings that were treated with MBF also began to significantly increase their leaf dry weight of about 58% with respect to the control (Figure 1A). Finally, from 15 days (T15) to the end of the experiment (T20), the MBF effect on the fresh weights of the leaves was comparable to the effect induced by Seq, showing an increase in the final fresh weight of around 62% compared to the control (Figure 1A). On the contrary, the inoculum (In) showed a significantly effect than the control only at the end of the experimental period (T20), although it was always significantly lower than treatments with Seq and MBF (Figure 1A).
With regards to the root fresh weights, Figure 1B shows an evident effect due to microorganism action of MBF (MBF and In). The plants treated with Seq showed root fresh weights statistically not significant with respect to the plants treated with MBF and In, except at the time T10, in which the root fresh weights of seedlings treated with Seq were lower than those measured in strawberries treated with BMF and In (Figure 1B).
The leaf dry weights (Figure 2A) showed that sequestrene seems to be the best treatment, showing at T20 a significant increase with respect to all the others (around 180%, 32%. and 101% for CNT, MBF, and In, respectively) (Figure 2A). As regards the root dry weights, the trend observed was very similar to that observed for fresh weights (Figure 2B).
Figure 3A,B shows the iron content (g Kg−1 dry matter) in the leaves and root during the experimental trials. As expected, the highest values were registered for Seq and MBF treatments, both in leaves and in roots, with values similar for the two theses, except at the time T5 (Figure 3A,B), in which the Seq treatment drastically increased the iron level in both tissues. As a consequence of iron content increase in leaves (Figure 3), total chlorophyll contents (Figure 4) in seedlings treated with Seq and MBF have shown significantly higher values with respect to the control and In, recording a percentage increase of 177% and 180%, respectively. The only exception was found at the time T5, at which point chlorophylls in the leaves treated with Seq were significantly higher than those measured in plants treated with MBF (Figure 4). The increase in the iron and chlorophyll contents was immediately evident at the visual analysis of the leaves of treated and untreated strawberry seedlings (Figure 5).
The enzymatic results of FC-R activities are shown in Figure 6. The results were consistent with the increased enzymatic activity in the control thesis subjected to chlorosis during the experimental period. In contrast, the roots treated with Seq and MBF showed, already at 5 days after the treatment, enzymatic activity values that were similar among them, and significantly lower with respect to the control and In (Figure 6). However, at 15 and 20 days after the treatments, the In-treated plants showed values significantly lower than those measured in the control, although these activities were always higher than those obtained with Seq and MBF treatments (Figure 6).

4. Discussion

Many authors have focused on the study of the most appropriate strategies to overcome the iron deficiency chlorosis in strawberries [43,44,45,46,47]. In our experimental work, sequestrene efficiently counteracted, within 20 days, the iron deficiency induced in strawberries, in accordance with the evidence that iron chelates are the most widely accepted methods to overcome chlorosis [45,48,49]. The effects of treatments in iron deficiency conditions were evaluated by monitoring several parameters associated to chlorosis, and often involving secondary effects resulting from the complex interactions of Fe with other elements and various soil and environmental factors [50]. These results showed that the treatment with MBF was highly efficient in mitigating the effects of Fe-deficiency induced in strawberry seedlings, reaching results comparable to those obtained using sequestrene at the end of the experimental period by increasing fresh and dry weights (Figure 1 and Figure 2), the absorption of iron (Figure 3), and the chlorophyll content (Figure 4). These data also suggest that a different mechanism of action on the strawberry occurred between MBF and sequestrene. Indeed, already five days after the treatment, sequestrene induced a fast response when compared to treatment with MBF, resulting in a greater growth, above all at leaf dry weight level (Figure 2A). These results are in accordance with Gilbert [51], who found that when iron deficiency occurs in strawberries, sequestrene can alleviate the negative effects within few days. These prompt effects of sequestrene may be partially attributed to the presence of the commercial formulation of nitrogen and potassium (as detailed in Materials and Methods), which is readily available for the plants. Moreover, the recovery of chlorotic strawberry plants rapidly occurs in response to the availability of iron [38].
The effects on evaluated parameters of strawberry plants treated with MBF were slightly delayed by about five days, which was presumably related to the evidence that in this case the overcoming chlorosis effects was exclusively due to the greater availability of iron generated by the synergy between the inoculated telluric microorganisms, occurring in the commercial formulation, and the presence of available and potentially available iron. On the other hand, in strawberry plants treated only with the inoculum (In), the overcoming effects were slower than the complete commercial formulation (MBF). Therefore, these results suggest that strawberry plants, in this case, were able to use only the native iron of the soil, made available by the phytosiderophores produced by microorganisms present in the inoculum. Although the complete formulation of MBF raised better results, the formulation containing only the microorganisms (In) also acted against chlorosis effects when compared to the control (Figure 1, Figure 2, Figure 3, Figure 4 and Figure 5). In particular, the mainly evident effects concerning root parameters (Figure 1B, Figure 2B, Figure 3B and Figure 6) were probably due to the mycorrhized roots, which putatively can have a significant benefit in counteracting Fe-deficiency. Therefore, the positive effects against chlorosis observed in strawberry plants treated with MBF and In, above all at root level, might be due to a microorganisms-mediated action of these formulations. This hypothesis is supported by Spinelli et al. [47], who found that the treatment of strawberry plants with a commercial biostimulant seaweed extract (Actiwave®) may counteract the effect of chlorosis, reaching results very similar to sequestrene action, by increasing shoot and root dry matter and positively influencing the root associated microbial community [47].
Although to a different extent, both the alternative treatment methods to sequestrene performed on strawberry plants induced metabolic changes, able to counteract chlorosis within a few days or weeks. Similar results were also obtained by resupplying iron in spinach and sugar beet, leading to an increase in chlorophyll concentration and the rate of photosynthesis within few days [52,53,54]. Strategy I plants, such as strawberries, respond to Fe-deficiency by increasing their ability to reduce Fe (III) to Fe (II), which can be then taken up by a Fe(II) transporter and absorbed by the root. Consequently, the values of Fe chelate reductase activity (FC-R) increase in the roots [12]. Our results showed that FC-R activity increased in control plants along with the experimental ones (Figure 6), underlying the tendency to respond by using strategy I to address Fe-deficiency due to the worsening of chlorotic conditions in untreated strawberry plants. On the contrary, all the performed treatments reduced the values of FC-R activities along with the experimental ones, in accordance with a reduction of chlorosis symptoms (Figure 5 and Figure 6). These results are supported by Pestana et al. [38], who found smaller FC-R activities in chlorotic strawberry plants treated by foliar spray to supply Fe with respect to the untreated control within few days. The complete formulation of MBF and sequestrene quickly lowered FC-R activity values, coupled with a reduction of chlorosis symptoms (Figure 5). As regards the In treatment, the effectiveness in alleviating chlorosis symptoms was later as well as lower than the complete formulation, however after 15 days, strawberry plants coped with the Fe-deficiency. These results are also supported by Ipek et al. [55], who found that a plant-growth-promoting rhizobacteria (PGPR) treatment was able to increase plant resistance in high calcareous soil conditions.

5. Conclusions

In conclusion, microorganism-based formulations may represent a valid alternative to sequestrene in strawberry production. An important role is represented by the microorganism inoculum. Nonetheless, the use of these microorganism-based formulations must be combined with all the agronomic practices able to minimize the Fe-deficiency and maximize the potential of a crop plant, production, quality, and safety, in order to lower synthetic organic, chelate use and reduce the impacts on the environment.

Author Contributions

I.P., S.B. and V.S. conducted the field experiment and determinations; V.T. and A.B. were involved in laboratory analyses; V.S. and I.P. contributed to statistical data processing and interpretation; V.S., A.B. and I.P. conceived and planned the experimental protocol, and performed the research supervision; I.P., S.B. and V.M.S. were involved in bibliographic search; I.P., V.S., V.M.S. and A.B. wrote the draft and final manuscript. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

All data are reported in the manuscript therefore this statement can be excluded.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Abadía, J.; Vázquez, S.; Rellán-Álvarez, R.; El-Jendoubi, H.; Abadía, A.; Álvarez-Fernández, A.; López-Millán, A.F. Towards a knowledge-based correction of iron chlorosis. Plant Physiol. Biochem. 2011, 49, 471–482. [Google Scholar] [CrossRef]
  2. Pushnik, J.C.; Miller, G.W. Iron regulation of chloroplast photosynthetic function: Mediation of PS-I development. J. Plant Nutr. 1989, 12, 407–421. [Google Scholar] [CrossRef]
  3. Terry, N.; Abadia, J. Function of iron in chloroplast. J. Plant Nutr. 1986, 9, 609–646. [Google Scholar] [CrossRef] [Green Version]
  4. Rutherford, A.W. Photosystem II, the water-splitting enzyme. Trends Biochem. Sci. 1989, 14, 227–232. [Google Scholar] [CrossRef]
  5. Abadia, J.; Abadia, A. Iron and plant pigments. In Iron Chelation in Plants and Soil Microorganisms; Barton, L.L., Hemming, B.C., Eds.; Academic Press: San Diego, CA, USA, 1993; pp. 327–343. [Google Scholar]
  6. Spiller, S.; Terry, N. Limiting factors in photosynthesis. 2. Iron stress diminished photochemical capacity by reducing the number of photosynthetic units. Plant Physiol. 1980, 65, 121–125. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  7. Kabata-Pendias, A. Trace Elements in Soils and Plants; CRC: Boca Raton, FL, USA, 2001; pp. 76–78. [Google Scholar]
  8. Coulombe, B.A.; Chaney, R.L.; Wiebold, W.J. Bicarbonate directly induces iron chlorosis in susceptible soybean cultivars. Soil Sci. Soc. Amer. J. 1984, 48, 1297–1301. [Google Scholar] [CrossRef]
  9. Römheld, V.; Marschner, H. Evidence for a specific uptake system for iron phytosiderophores in roots of grasses. Plant Physiol. 1986, 80, 175–180. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  10. Stephan, U.W. Intra- and intercellular iron trafficking and subcellular compartmentation within roots. Plant Soil 2002, 241, 19–25. [Google Scholar] [CrossRef]
  11. Imtiaz, M.; Rashid, A.; Khan, P.; Memon, M.Y.; Aslam, M. The role of micronutrients in crop production and human health. Pak. J. Bot. 2010, 42, 2565–2578. [Google Scholar]
  12. Taiz, L.; Zeiger, E. Plant Physiology, 4th ed.; Sinauer Associates, Inc.: Sunderland, MA, USA, 2006. [Google Scholar]
  13. Cesco, S.; Nikolic, M.; Romheld, V.; Varanini, Z.; Pinton, R. Uptake of Fe-59 from soluble Fe-59-humate complexes by cucumber and barley plants. Plant Soil 2002, 241, 121–128. [Google Scholar] [CrossRef]
  14. Toulon, V.; Sentenac, H.; Thibaud, J.B.; Davidian, J.C.; Moulineaz, C.; Grignon, C. Role of apoplast acidification by H+ pump. Effect on the sensitivity to pH and CO2 of iron reduction by roots of Brassica napus L. Planta 1992, 186, 212–218. [Google Scholar] [PubMed]
  15. Marschner, H. Mineral Nutrition of Higher Plants, 3rd ed.; Academic Press: Hohenheim, Germany, 2011. [Google Scholar]
  16. Zanin, L.; Tomasi, N.; Cesco, S.; Varanini, Z.; Pinton, R. Humic substances contribute to plant iron nutrition acting as chelators and biostimulants. Front. Plant Sci. 2019, 675, 1–10. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  17. Baglieri, A.; Borzí, D.; Abbate, C.; Ńegre, M.; Gennari, M. Removal of fenhexamid and pyrimethanil from aqueous solutions by clays and organoclays. J. Environ. Sci. Health Part B 2009, 44, 220–225. [Google Scholar] [CrossRef] [PubMed]
  18. Zhao, L.; Wang, Y.; Kong, S. Effects of Trichoderma asperellum and its siderophores on endogenous auxin in Arabidopsis thaliana under iron-deficiency stress. Int. Microbiol. 2020, 23, 501–509. [Google Scholar] [CrossRef] [PubMed]
  19. Dimkpa, C.; Svatos, A.; Merten, D.; Buchel, G.; Kothe, E. Hydroxamate siderophores produced by Streptomyces acidiscabies E13 bind nickel and promote growth in cowpea (Vigna unguiculata L.) under nickel stress. Can. J. Microbiol. 2008, 54, 163–172. [Google Scholar] [CrossRef] [PubMed]
  20. Siebner-Freibach, H.; Yariv, S.; Lapides, Y.; Hadar, Y.; Chen, Y. Thermo-FTIR spectroscopic study of the siderophore ferrioxamine B: Spectral analysis and stereochemical implications of iron chelation, pH, and temperature. J. Agric. Food Chem. 2005, 53, 3434–3443. [Google Scholar] [CrossRef]
  21. Colombo, C.; Palumbo, G.; He, J.Z.; Pinton, R.; Cesco, S. Review on iron availability in soil: Interaction of Fe minerals, plants, and microbes. J. Soils Sediments 2014, 14, 538–548. [Google Scholar] [CrossRef]
  22. Abbate, C.; Borzì, D.; Caboni, P.; Baglieri, A.; Gennari, M. Behavior of fenhexamid in soil and water. J. Environ. Sci. Health Part B 2007, 42, 843–849. [Google Scholar] [CrossRef] [PubMed]
  23. Zhao, L.; Zhang, Y.Q. Effects of phosphate solubilization and phytohormone production of Trichoderma asperellum Q1 on promoting cucumber growth under salt stress. J. Integr. Agric. 2015, 14, 1588–1597. [Google Scholar] [CrossRef] [Green Version]
  24. Jin, C.W.; Ye, Y.Q.; Zheng, S.J. An underground tale: Contribution of microbial activity to plant iron acquisition via ecological processes. Ann. Bot. 2013, 113, 7–18. [Google Scholar] [CrossRef] [Green Version]
  25. Schalk, I.J.; Hannauer, M.; Braud, A. New roles for bacterial siderophores in metal transport and tolerance. Environ. Microbiol. 2011, 13, 2844–2854. [Google Scholar] [CrossRef]
  26. Tagliavini, M.; Scudellari, D.; Marangoni, B.; Toselli, M. Nitrogen fertilization management in orchards to reconcile productivity and environmental aspects. Fertil. Res. 1996, 43, 93–102. [Google Scholar] [CrossRef]
  27. Tagliavini, M.; Baldi, E.; Lucchi, P.; Antonelli, M.; Sorrenti, G.; Baruzzi, G.; Faedi, W. Dynamics of nutrients uptake by strawberry plants (Fragaria × ananassa Dutch.) grown in soil and soilless culture. Eur. J. Agron. 2005, 23, 15–25. [Google Scholar] [CrossRef]
  28. Cojocaru, A.; Munteanu, N.; Petre, B.A.; Stan, T.; Teliban, G.C.; Vintu, C.; Stoleru, V. Biochemical and production of Rhubarb under growing technological factors. Rev. Chim. 2019, 70, 2000–2003. [Google Scholar] [CrossRef]
  29. Stoleru, V.; Munteanu, N.; Sellitto, V.M. New Approach of Organic Vegetable Systems; Aracne Editrice: Rome, Italy, 2014; pp. 56–71. [Google Scholar]
  30. Cojocaru, A.; Vlase, L.; Munteanu, N.; Stan, T.; Teliban, G.C.; Burducea, M.; Stoleru, V. Dynamic of phenolic compounds, antioxidant activity, and yield of Rhubarb under chemical, organic and biological fertilization. Plants 2020, 9, 355. [Google Scholar] [CrossRef]
  31. FAO. The Future of Food and Agriculture—Trends and Challenges; FAO: Rome, Italy, 2017. [Google Scholar]
  32. Barone, V.; Puglisi, I.; Fragalà, F.; Lo Piero, A.R.; Giuffrida, F.; Baglieri, A. Novel bioprocess for the cultivation of microalgae in hydroponic growing system of tomato plants. J. Appl. Phycol. 2019, 31, 465–470. [Google Scholar] [CrossRef]
  33. Violante, P. Metodi di analisi chimica del suolo. In Collana di Metodi Analitici per L’agricoltura; Sequi, P., Ed.; Francoangeli: Milano, Italy, 2000; pp. 46–51. [Google Scholar]
  34. Barone, V.; Puglisi, I.; Fragalà, F.; Stevanato, P.; Baglieri, A. Effect of living cells of microalgae or their extracts on soil enzyme activities. Arch. Agron. Soil Sci. 2019, 65, 712–726. [Google Scholar] [CrossRef]
  35. Puglisi, I.; Nicolosi, E.; Vanella, D.; Lo Piero, A.R.; Stagno, F.; Saitta, D.; Roccuzzo, G.; Consoli, S.; Baglieri, A. Physiological and biochemical responses of orange trees to different deficit irrigation regimes. Plants 2019, 8, 423. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  36. Vanni, A.; Anfossi, L.; Cignetti, A.; Baglieri, A.; Gennari, M. Degradation of pyrimethanil in soil: Influence of light, oxygen, and microbial activity. J. Environ. Sci. Health Part B 2006, 41, 67–80. [Google Scholar] [CrossRef]
  37. Puglisi, I.; La Bella, E.; Rovetto, E.I.; Lo Piero, A.R.; Baglieri, A. Biostimulant effect and biochemical response in lettuce seedlings treated with a Scenedesmus quadricauda extract. Plants 2020, 9, 123. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  38. Pestana, M.; Correia, P.J.; Saavedra, T.; Gama, F.; Abadía, A.; de Varennes, A. Development and recovery of iron deficiency by iron resupply to roots or leaves of strawberry plants. Plant Physiol. Biochem. 2012, 53, 1–5. [Google Scholar] [CrossRef] [PubMed]
  39. Puglisi, I.; Barone, V.; Sidella, S.; Coppa, M.; Broccanello, C.; Gennari, M.; Baglieri, A. Biostimulant activity of humic-like substances from agro-industrial waste on Chlorella vulgaris and Scenedesmus quadricauda. Eur. J. Phycol. 2018, 53, 433–442. [Google Scholar] [CrossRef]
  40. Barone, V.; Bertoldo, G.; Magro, F.; Broccanello, C.; Puglisi, I.; Baglieri, A.; Cagnin, M.; Concheri, G.; Squartini, A.; Pizzeghello, D.; et al. Molecular and morphological changes induced by Leonardite-based biostimulant in Beta vulgaris L. Plants 2019, 8, 181. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  41. Bienfait, H.F.; Bino, R.J.; Vanderbliek, A.M.; Duivenvoorden, J.F.; Fontaine, J.M. Characterization of ferric reducing activity in roots of Fe-deficient Phaseolus vulgaris. Physiol. Plant. 1983, 59, 196–202. [Google Scholar] [CrossRef]
  42. Puglisi, I.; De Patrizio, A.; Schena, L.; Jung, T.; Evoli, M.; Pane, A.; Hoa, N.V.; Tri, M.V.; Wright, S.; Ramstedt, M.; et al. Two previously unknown Phytophthora species associated with brown rot of Pomelo (Citrus grandis) fruits in Vietnam. PLoS ONE 2017, 12, e0172085. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  43. Erdal, I.; Kepenek, K.; Kizigöz, I. Effect of elemental sulphur and sulphur containing waste on the iron nutrition of strawberry plants grown in calcareous soil. Biol. Agric. Hortic. 2006, 23, 263–272. [Google Scholar] [CrossRef]
  44. Peris-Felipo, F.J.; Benavent-Gil, Y.; Hernandez-Apaolaza, L. Silicon beneficial effects on yield, fruit quality and shelf-life of strawberries grown in different culture substrates under different iron status. Plant Physiol. Biochem. 2020, 152, 23–31. [Google Scholar] [CrossRef] [PubMed]
  45. Zaiter, H.Z.; Saad, I.; Nimah, M. Yield of iron-sprayed and non-sprayed strawberry cultivars grown on high calcareous soil. J. Plant Nutr. 1993, 16, 281–296. [Google Scholar] [CrossRef]
  46. Türemis, N.; Ozguven, A.L.; Paydas, S.; Idem, G. Effects of sequestrene Fe-138 as foliar and soil application on yield and earliness of some strawberry cultivars in the subtropics. Acta Hortic. 1997, 441, 369–374. [Google Scholar] [CrossRef]
  47. Spinelli, F.; Fiori, G.; Noferini, M.; Sprocatti, M.; Costa, G. A novel type of seaweed extract as a natural alternative to the use of iron chelates in strawberry production. Sci. Hortic. 2010, 125, 263–269. [Google Scholar] [CrossRef]
  48. Lucena, J.J.; Garate, A.; Ramon, A.M.; Manzanares, M. Iron nutrition of a hydroponic strawberry culture (Fragaria vesca L.) supplied with different Fe chelates. Plant Soil 1990, 123, 9–15. [Google Scholar] [CrossRef]
  49. Abadia, J.; Álvarez-Fernández, A.; Morales, F.; Sanz, M.; Abadia, A. Correction of iron chlorosis by foliar sprays. Acta Hortic. 2002, 594, 115–121. [Google Scholar] [CrossRef]
  50. Erdal, I.; Kepenek, K.; Kizigöz, I. Effect of foliar iron applications at different growth stages on iron and some nutrient concentrations in strawberry. Turk. J. Agric. For. 2004, 28, 421–427. [Google Scholar]
  51. Gilbert, E. A Guide to Soft Fruit Growing—The Strawberry; Codman Press: Boston, MA, USA, 2013. [Google Scholar]
  52. Timperio, A.M.; D’Amici, G.M.; Barta, C.; Loreto, G.M.; Zolla, L. Proteomics, pigment composition, and organization of thylakoid membranes in iron-deficient spinach leaves. J. Exp. Bot. 2006, 58, 3695–3710. [Google Scholar] [CrossRef] [Green Version]
  53. Larbi, A.; Abadía, A.; Morales, F.; Abadía, J. Fe resupply to Fe-deficient sugar beet plants leads to rapid changes in the violaxanthin cycle and other photosynthetic characteristics without significant de novo chlorophyll synthesis. Photosynth. Res. 2004, 79, 59–69. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  54. Hajizadeh, H.S.; Heidari, B.; Bertoldo, G.; Della Lucia, M.C.; Magro, F.; Broccanello, C.; Baglieri, A.; Puglisi, I.; Squartini, A.; Campagna, G.; et al. Expression profiling of candidate genes in sugar beet leaves treated with Leonardite-based biostimulant. High-Throughput 2019, 8, 18. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  55. Ipek, M.; Pirlak, L.; Esitken, A.; Donmez, M.F.; Turan, M.; Sahin, F. Plant Growth-Promoting Rhizobacteria (PGPR) increase yield, growth and nutrition of strawberry under high-calcareous soil conditions. J. Plant Nutr. 2014, 37, 990–1001. [Google Scholar] [CrossRef]
Figure 1. Fresh weights (g) of leaves (A) and roots (B) of strawberry plants. Error bars indicate standard deviation (n = 5). Sampling was performed at T0 (before treatments), T5 (5 days after the treatment), T10 (10 days after the treatment), T15 (15 days after the treatment), T20 (20 days after the treatment). CNT: control, Seq: sequestrene, MBF: microorganism-based formulation, In: inoculum of MBF. Values within each sampling time followed by different letters are significantly different (p < 0.05).
Figure 1. Fresh weights (g) of leaves (A) and roots (B) of strawberry plants. Error bars indicate standard deviation (n = 5). Sampling was performed at T0 (before treatments), T5 (5 days after the treatment), T10 (10 days after the treatment), T15 (15 days after the treatment), T20 (20 days after the treatment). CNT: control, Seq: sequestrene, MBF: microorganism-based formulation, In: inoculum of MBF. Values within each sampling time followed by different letters are significantly different (p < 0.05).
Agriculture 11 00217 g001
Figure 2. Dry weights (g) of leaves (A) and roots (B) of strawberry plants. Error bars indicate standard deviation (n = 5). Sampling was performed at T0 (before treatments), T5 (5 days after the treatment), T10 (10 days after the treatment), T15 (15 days after the treatment), T20 (20 days after the treatment). CNT: control, Seq: sequestrene, MBF: microorganism-based formulation, In: inoculum of MBF. Values within each sampling time followed by different letters are significantly different (p < 0.05).
Figure 2. Dry weights (g) of leaves (A) and roots (B) of strawberry plants. Error bars indicate standard deviation (n = 5). Sampling was performed at T0 (before treatments), T5 (5 days after the treatment), T10 (10 days after the treatment), T15 (15 days after the treatment), T20 (20 days after the treatment). CNT: control, Seq: sequestrene, MBF: microorganism-based formulation, In: inoculum of MBF. Values within each sampling time followed by different letters are significantly different (p < 0.05).
Agriculture 11 00217 g002
Figure 3. Iron content (mg kg−1 ss) in leaves (A) and roots (B) of strawberry plants. Error bars indicate standard deviation (n = 5). Sampling was performed at T0 (before treatments), T5 (5 days after the treatment), T10 (10 days after the treatment), T15 (15 days after the treatment), T20 (20 days after the treatment). CNT: control, Seq: sequestrene, MBF: microorganism-based formulation, In: inoculum of MBF. Values within each sampling time followed by different letters are significantly different (p < 0.05).
Figure 3. Iron content (mg kg−1 ss) in leaves (A) and roots (B) of strawberry plants. Error bars indicate standard deviation (n = 5). Sampling was performed at T0 (before treatments), T5 (5 days after the treatment), T10 (10 days after the treatment), T15 (15 days after the treatment), T20 (20 days after the treatment). CNT: control, Seq: sequestrene, MBF: microorganism-based formulation, In: inoculum of MBF. Values within each sampling time followed by different letters are significantly different (p < 0.05).
Agriculture 11 00217 g003
Figure 4. Chlorophyll content (μmoles m−2) in leaves of strawberry plants. Error bars indicate standard deviation (n = 5). Sampling was performed at T0 (before treatments), T5 (5 days after the treatment), T10 (10 days after the treatment), T15 (15 days after the treatment), T20 (20 days after the treatment). CNT: control, Seq: sequestrene, MBF: microorganism-based formulation, In: inoculum of MBF. Values within each sampling time followed by different letters are significantly different (p < 0.05).
Figure 4. Chlorophyll content (μmoles m−2) in leaves of strawberry plants. Error bars indicate standard deviation (n = 5). Sampling was performed at T0 (before treatments), T5 (5 days after the treatment), T10 (10 days after the treatment), T15 (15 days after the treatment), T20 (20 days after the treatment). CNT: control, Seq: sequestrene, MBF: microorganism-based formulation, In: inoculum of MBF. Values within each sampling time followed by different letters are significantly different (p < 0.05).
Agriculture 11 00217 g004
Figure 5. Chlorosis symptoms in leaves of strawberry plants at T0 (before treatment) and T20 (20 days after treatment).
Figure 5. Chlorosis symptoms in leaves of strawberry plants at T0 (before treatment) and T20 (20 days after treatment).
Agriculture 11 00217 g005
Figure 6. Fe chelate reductase activity (FC-R) in roots of strawberry plants. Error bars indicate standard deviation (n = 5). Sampling was performed at T0 (before treatments), T5 (5 days after the treatment), T10 (10 days after the treatment), T15 (15 days after the treatment); T20 (20 days after the treatment). CNT: control, Seq: sequestrene, MBF: Microorganism-based formulation, In: inoculum of MBF. Values within each sampling time followed by different letters are significantly different (p < 0.05).
Figure 6. Fe chelate reductase activity (FC-R) in roots of strawberry plants. Error bars indicate standard deviation (n = 5). Sampling was performed at T0 (before treatments), T5 (5 days after the treatment), T10 (10 days after the treatment), T15 (15 days after the treatment); T20 (20 days after the treatment). CNT: control, Seq: sequestrene, MBF: Microorganism-based formulation, In: inoculum of MBF. Values within each sampling time followed by different letters are significantly different (p < 0.05).
Agriculture 11 00217 g006
Table 1. Characteristics of soil subjected to the experimental design.
Table 1. Characteristics of soil subjected to the experimental design.
Soil PropertiesPre-Treatment
pH8.1 ± 0.2
E.C (dS/m)0.179 ± 0.010
CEC (meq/100 g)18 ± 1.1
O.M. (%)2.0 * ± 0.8
O.C. (%)1.14 * ± 0.6
Active CaCO3 (%)19.5 ± 1.2
Total CaCO3 (%)37.1 ± 3.2
Total Fe (mg/kg)665 ± 21
Extractable Fe (mg/kg)41.38 ± 5.3
Available Fe (mg/kg)1.96 ± 0.2
Readily available Fe (mg/kg)0.20 ± 0.02
CPI113.9 ± 10
* O.M: 1.7% before amendment; O.C: 0.97% before amendment.
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Puglisi, I.; Brida, S.; Stoleru, V.; Torino, V.; Sellitto, V.M.; Baglieri, A. Application of Novel Microorganism-Based Formulations as Alternative to the Use of Iron Chelates in Strawberry Cultivation. Agriculture 2021, 11, 217. https://0-doi-org.brum.beds.ac.uk/10.3390/agriculture11030217

AMA Style

Puglisi I, Brida S, Stoleru V, Torino V, Sellitto VM, Baglieri A. Application of Novel Microorganism-Based Formulations as Alternative to the Use of Iron Chelates in Strawberry Cultivation. Agriculture. 2021; 11(3):217. https://0-doi-org.brum.beds.ac.uk/10.3390/agriculture11030217

Chicago/Turabian Style

Puglisi, Ivana, Sergio Brida, Vasile Stoleru, Valentina Torino, Vincenzo Michele Sellitto, and Andrea Baglieri. 2021. "Application of Novel Microorganism-Based Formulations as Alternative to the Use of Iron Chelates in Strawberry Cultivation" Agriculture 11, no. 3: 217. https://0-doi-org.brum.beds.ac.uk/10.3390/agriculture11030217

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop