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    • 专利摘要:
    Method for the disinfection of agricultural soils. A method for disinfecting soils or other agricultural crop substrates, characterized in that it comprises: obtaining a soil or other agricultural crop substrate at its field capacity; treat the soil or substrate at field capacity of the previous stage with ozonated water, where the ozonated water is prepared in situ with an ozone production equipment connected to the water supply; allow time for ozone treatment to elapse; and inoculate the soil or agricultural substrate disinfected with at least one species of beneficial microorganism. (Machine-translation by Google Translate, not legally binding)
    公开号:ES2625034A1
    申请号:ES201630043
    申请日:2016-01-18
    公开日:2017-07-18
    发明作者:Emilio Jesus VILLANUEVA DECODES
    申请人:Emilio Jesus VILLANUEVA DECODES；
    IPC主号:
    专利说明:

    DESCRIPTION

    METHOD FOR DISINFECTION OF AGRICULTURAL SOILS

    SECTOR OF THE TECHNIQUE 5

    The present patent application describes a method for disinfecting soils and other agricultural cultivation substrates by using ozone, in particular ozonated water generated at the place and time of application.
     10
    BACKGROUND

    Climate change, population growth, and the imminent shortage of natural resources, make it necessary to change traditional agricultural production models and replace them with more sustainable production systems. fifteen

    On the other hand, since 1840 it is known that ozone is the most potent oxidant that exists. Additionally, its efficiency as a germicidal and bactericidal agent has also been demonstrated with various studies. In agriculture, ozone has been shown to provide additional benefits, both for cultivation and for the grower, such as: greater plant growth, shorter fruit ripening time, greater production and taste, and lower risk of disease.

    Until recently, the use of methyl bromide, a very effective and widely known compound, has been allowed. Since its ban, other chemicals registered as Chloropicrin, 1-3 Dichloropropene or a mixture of both (Agrocelhone), Metam ‐ sodium, Metam ‐ potassium, Methyl thioisocyanate are being used. However, all these products must be handled by accredited personnel according to RD 1311/2012, they are dangerous for people, the environment, especially surface and groundwater, and the safety period for plantations is more than one month, must have during that time the 30 unproductive soil.

    On the other hand, the disinfection methods used to date in agriculture use chemical additives that cause waste. This is not the case in the use of ozone to
    disinfect soils or substrates for agricultural use and, therefore, it is not necessary to establish a waiting period until they are put into cultivation.

    However, the instability of ozone in the environment means that storage is not possible and that it must be produced on demand at the place of application, which requires a high energy demand, which is a great inconvenience. For this reason, to date there are no known methods that allow effective soil disinfection using ozone.

    Artificial ozone generation is generally done by activating oxygen 10 in the air by high-voltage electrical discharges. This electrical energy breaks the oxygen molecule, recombining its atoms to form OZONE. In the same way that Nature does in storms.

    The release of energy when generating ozone is an endothermic process, whose energy comes from the electric discharge. In the same way, ozone decomposes spontaneously into diatomic oxygen, releasing excess energy, so it must be generated at the time and place of its immediate use. For this, equipment called “ozonizers” or ozone generators are used.
     twenty
    Since the end of the 19th century, ozone disinfectant and antiseptic properties have been studied and since then it has been used with great efficiency in environmental treatments. Its ability to break molecules with double bond and aromatic rings by means of the mechanism called ozonolysis, make ozone have many applications, including bactericide, viricide, fungicide and deodorant; 25 rapidly destroying streptococci, staphylococci, colibacils, etc., as well as the most energetic diphtheria and tetanus toxins.

    Generally, ozone is used to carry out one or more of the following fundamental functions: microbicide, deodorant and oxygenator. Among them, microbicidal activity is perhaps the most important property of ozone. Due to its oxidizing properties, ozone can be considered as one of the fastest and most effective microbicidal agents known. Its action has a broad spectrum that includes the elimination of bacteria, fungi, viruses and nematodes.
     35
    Additionally, ozone is also often used for its deodorant activity, being very useful in all types of public use premises and in the treatment of certain odors of industrial origin, smell of people, moisture, tobacco, food, etc. On the one hand, ozone oxidizes organic matter (ozonolysis) and, on the other hand, attacks the microbes that feed on it. There is a wide range of odors that can be attacked by ozone. 5

    In large cities, where there are a large number of closed and poorly ventilated premises, air thinning is very often noticeable as a result of a lack of oxygen, which we usually identify as stale air. Ozone, due to its greater oxygenating power, helps to improve the efficiency of the 10 cells of higher organisms in terms of the use of available oxygen, by stimulating several enzymes involved in these processes. In addition, the decomposition of ozone is necessarily in oxygen, which will be located where the ozone gas has penetrated, in the air, in the water, or underground.
     fifteen
    As mentioned above, the ozone disinfection action is produced by oxidation. Under conditions of low pH by molecular oxidation and in high pH media by oxidation by hydroxyls. Because of these oxidizing properties, ozone is considered one of the fastest and most effective microbicidal agents known.
     twenty
    As an alternative method to the use of ozone, disinfection methods based on the use of chlorine are also known in the state of the art. In this type of process, the disinfectant action occurs when the chlorine spreads through the cell walls and oxidizes the enzyme and, consequently, they are slow disinfection methods. However, ozone-based disinfection methods are advantageous, since in these methods cell membranes are destroyed or decomposed in a very rapid process where, as an additional advantage, ozone is inactivated into oxygen. More specifically, ozone acts on the cell wall of the microorganism degrading it, which creates a "hole" through which it loses its cellular fluid. Ozone disinfection is called bacteriolysis. 30

    Additionally, ozone-based treatments require a residual dose of disinfectant and a significantly shorter application period than in disinfection methods based on chemical additives such as chlorine. Thus, a residual ozone dose of 0.1mg / l for 5 seconds is generally necessary, compared to 4 hours 35
    necessary for chlorine. It has also been determined that ppm of ozone is needed for four minutes to eliminate microorganisms. Ozone can also kill 99% of 60,000 coliforms / ml in contaminated water in 2.8 seconds with a dose of ppm, with the same dose of chlorine 15,000 seconds are needed.
     5
    Another significant advantage of using ozone in the elimination of microorganisms is that resistance is not produced because its mechanism of action is based on the rupture of the cell wall. Generally, aerobic spore bacteria disinfect more easily than anaerobic spore bacteria. The effectiveness of disinfection in solution is higher against lactic acid bacteria and, therefore, also against fungal yeast.

    In Figure 1 we see the necessary time that the pathogen has to be in contact with ozone, either in the air or mixed with water, to be destroyed.
     fifteen
    As mentioned earlier, ozone disinfectant properties are widely known. Also, methods for disinfecting air or water using this compound are also known. However, although water disinfected with ozone has sometimes been used as irrigation water, so far there is no known effective method to disinfect soils and other agricultural crop substrates using ozone as a disinfectant.

    DESCRIPTION

    In a first aspect, the present patent application refers to a method for disinfecting soils or other agricultural cultivation substrates, characterized in that it comprises:
    - obtain a soil or other agricultural crop substrate at its field capacity;
    - treat the soil or substrate at field capacity of the previous stage with ozonated water containing min. 2 ppm of ozone, preferably between 5 and 6 ppm of ozone, where ozonated water is prepared on site with an ozone production equipment connected to the water supply with a pH between 5.0 and 8.5, preferably the treatment with ozone it is applied for between 1 h 30 min and 2 hours; and
    - leave between 30 min and 24 hours after the ozone treatment; and
    - inoculate the soil or agricultural substrate disinfected with at least one kind of beneficial microorganism. 35

    The use of ozone in soil disinfection implies a series of technical problems that had not been solved so far. In particular, there was no known effective system to produce the amount of ozone necessary for the treatment of the land in an economically viable way. On the other hand, because the useful life of ozone is only 5 minutes, it is necessary that the production of ozone can be carried out with mobility, that is, that ozone can be produced at the place of application and during treatment. In relation to the above, in order to achieve greater effectiveness of the disinfection treatment, it is preferred that the ozone production equipment be of small dimensions, capable of accessing the irrigation heads without difficulty. 10

    In the method of disinfection of soils or other agricultural cultivation substrates described in this patent application, the ozone in the form of gas is intimately mixed with the irrigation water to saturate the water with ozone gas, thus allowing its effective transport to the deepest layers of the soil. Preferably, the mixture of water and ozone takes place with ozone gas in the form of nanobubbles. Thus, in the method of the present invention, a much greater ozone mobility is obtained in the substrate than if ozone gas was injected directly, so that its implementation is much less complicated and expensive.

    In the present invention, "other agricultural cultivation substrates" means those substrates used in hydroponic agriculture, that is, crops where the roots grow in an artificial medium formed by various permeable materials capable of retaining moisture and nutrients.

    The ozone production equipment used in the disinfection method described in the present invention can be moved to the treatment site and also allows the modification of parameters such as:
    - the concentration of ozone produced, depending on the oxygen load,
    - ozone production by weight, depending on the current intensity used,
    - the time of application of the ozonation treatment, 30
    - the percentage of water / ozone mixture and the size of the gas bubbles in the mixture,
    - the pressure and flow of irrigation water at the equipment outlet.

    This versatility allows each treatment to be adapted to the specific conditions of the soil or substrate to be treated, in particular, the structure of the soil and the type and extent of the infection to be treated, 35
    as well as allowing the treatment conditions to be adapted to the quality of the irrigation water to be used.

    In preferred embodiments of the method of the present invention, the ozone production equipment comprises two main parts: in one of them ozone is produced from oxygen and, in the other, ozone is injected into the water network of irrigation, subsequently passing to a mixing tank.

    In the method for disinfecting agricultural cultivation soils and substrates described in this patent application, the use of AGR-60 ozonation equipment with a workflow of 3000 L / h, or AGRZ-800 is especially advantageous, with a work flow between 10,000-45,000 L / h and capable of treating cultivation surfaces of 1 Ha.

    An additional problem related to the use of ozone to disinfect soils or substrates for agricultural use is the low solubility of ozone in water, although this solubility is greater than that of oxygen, it is still complicated, like that of any mixed gas With a liquid.

    To solve this technical problem and achieve saturation of the irrigation water with ozone gas, the method for disinfecting soils or other agricultural substrates of the present invention includes the use of a mixing tank, where the size of the bubbles is reduced generated by injecting the gas into the irrigation water until the so-called nanobubbles are achieved. In this way, the ozone gas load carried by each liter of water is much higher than what could be achieved to date, allowing the use of a lower number of ozone generating reactors, as well as a lower power consumption and a decrease in the size of the equipment necessary to apply the treatment, allowing the mobility of said equipment.

    To obtain the ozone nanobubbles, a recirculation of the water mixed with ozone must be achieved through ceramic sieves, with a pressure between 1 and 6 30 atm, depending on the flow of irrigation water. For example, for a flow of 40,000 l a pressure of 3 atm is needed in the mixer. This pressure and flow rate can be regulated automatically by means of a piloted automatic valve.

    The use of ozone in low concentrations, in particular between 0.4 and less than 2 ppm, allows disinfecting the water used for treatment, since ozone does not only act as a deodorizer and oxidizer of dissolved organic substances, but also as a disinfectant .
     5
    As mentioned earlier, ozone is an oxidizing agent and a germicide. Consequently, it can be used for the oxidation of organic matter present in the water, resulting in odor and color in the treated water. Ozone is increasingly used as an oxidizing agent because of its efficiency, its REDOX potential is 2.07 eV. Thanks to its oxidizing potential, ozone has the advantage of reducing the time normally required for disinfection.

    The use of this type of ozonated water provides the crop with quality water, free of pathogens, but lacking disinfectant capacity in the soil, since the low ozone load is quickly inactivated on contact with the organic matter present in the soil. . Thus, the use of water with ozone at low concentrations (less than 2 ppm), whether for drip irrigation, such as fogging or micro-sprinkling, provides pathogen-free water, which allows plants to grow in a favorable environment and aseptic for culture. However, these conditions have a very short persistence, so it is necessary to water with this system practically continuously, which prevents the colonization of 20 beneficial microorganisms.

    However, the method described in this patent application allows to disinfect a soil or other agricultural crop substrate by treating it with water containing a sufficiently high amount of dissolved ozone, in particular, it contains an amount equal to or greater than 2 ppm. In this way, the method of the present invention allows to achieve, by means of specific applications of the treatment, not only the disinfection of the irrigation water, but also of the pipes used and of the soil or substrate of treated agricultural cultivation, since this method allows The ozonated water reaches the ground and penetrates deeply while maintaining its ozone charge and, therefore, its disinfectant power. 30

    The soil or substrate to be treated must be in field capacity before ozone treatment. Therefore, if necessary, water is previously applied to the soil or substrate until it reaches its field capacity, an amount that will depend on the
    characteristics and structure of the soil, for example, sandy, clayey; of the existing crop or to be implanted; of the irrigation system used and the irrigation habits of the farmer.

    Ozone in the form of gas has virtually no mobility in the soil, whether the soil is compacted or aerated. Once the ozone has been mixed with the irrigation water, it easily spreads over a soil in field capacity, reaching the ends of the irrigation bulb, in the case of emitters, or the deeper layers, in the case of sprinkling, quickly .

    The useful life of the ozone at a water temperature of 15ºC is 30 minutes, and at 25ºC it is 10 15 minutes, so we have to get the ozone produced through the pipes to the emitter and move through the ground in capacity to field to the outside of the irrigation bulb before it degrades and transforms into oxygen. The inventors have observed that, by applying the method of the present invention, the time necessary for draining water with ozone in a hydroponic culture is less than that useful life. fifteen

    In preferred embodiments of the present invention, the ozone treatment takes place for a period of time between 1 h 30 min and 2 hours, thus ensuring that the water with disinfectant load reaches the limits of the irrigation bulb, achieving the disinfection of existing microorganisms. twenty

    Taking into account that ozone disinfection does not generate resistance by the mode of action, the method of the present invention allows to achieve total disinfection of the treated soil or substrate. Once the ozone treatment is finished, the method comprises inoculating at least one kind of beneficial microorganism that colonizes that empty space again and thus prevents access to opportunistic pathogens. Preferably, these beneficial microorganisms are selected from the group consisting of Trichodermas, Bacillus, Azotobacter, Pseudomonas and any combination of the above.
     30
    Inoculation with beneficial microorganisms takes place between 30 min and 24 hours after the end of the ozone treatment. The minimum period of 30 min allows the degradation of residual ozone in oxygen before inoculation. On the other hand, the application of these microorganisms before 24 hours, allows to avoid that the treated area is exposed to a rapid entry of opportunistic pathogens that can become 35
    more aggressive and harmful than before disinfecting, since there will be no beneficial microorganisms that neutralize its effects.

    The application of water in the different stages of the method described in this patent application can be carried out by any procedure known to the person skilled in the art, preferably by localized irrigation or sprinkling. In particular, it is preferred that the contribution of water with ozone takes place by drip irrigation to the soil, since in this way a more effective disinfectant action occurs, eliminating bacteria, fungi, viruses and nematodes initially present in the soil or substrate to try. Preferably, the beneficial microorganisms are preferably applied in the disinfected bulb. 10

    In other preferred embodiments, the inoculation with microorganisms takes place by means of an injector located in the ozonation equipment.

    The effectiveness of the disinfection of the pathogen is influenced by the contact time, the ozone concentration, the temperature of the water used as a route of mobility, the pH and the dissolved organic and inorganic substances. So we can say that the power of disinfection increases with a low pH (preferably between 5.0 and 7.0; the optimum being a pH between 5.6 and 6.5) and with a low water temperature. The lower the temperature, the better the dissolution of the gas in the water, a range between 8 ° C and 25 ° C being preferred, more preferably between 10 ° C and 20 ° C, the optimum temperature being 15 ° C.

    In other preferred embodiments, the water used in the method described in this patent application, in particular, the irrigation water used in the ozonation stage, is exempt from additives such as mineral fertilizers or organic matter. In the method of the present invention, the treatment with ozonated water is most effective when the levels of organic matter in the pipes is low (preferably, REDOX values of the water between 600 mV and 1100 mV must be reached), the soil temperature and water are also low (preferably, between 10 and 20 ° C) and the pH is preferably between 5.0 and 7.0. 30

    In other preferred embodiments, the method for disinfecting soils or other substrates for agricultural cultivation is performed in a timely manner, and can be performed before or during cultivation. It is also possible to perform repeated ozone treatments, since this treatment does not generate harmful residues for the crop. 35

    Thus, the use of ozone as a disinfectant in the method for disinfecting soils or other substrates for agricultural cultivation of the present invention presents several important advantages. On the one hand, due to its oxidizing properties, ozone is considered one of the fastest and most effective microbial agents known. 5 Additionally, the use of ozone does not contaminate the treated soil or substrate, nor leave harmful residues. On the contrary, as its degradation product is oxygen, the use of ozone favors root development and plant growth.

    However, ozone generally degrades very quickly, which makes it very difficult to carry out treatments based on this compound. For example, in conditions of water without organic matter, pH 7 and a water temperature of 15 ° C, the degradation of ozone into oxygen occurs approximately 30 minutes after being generated. For this reason, it is especially advantageous that the method of the present invention allows the production of the necessary amount of ozone at the time and place where its disinfectant action is required.

    The method described in this patent application can be applied to soils or other substrates without cultivation in production. In these cases, the method preferably comprises the following steps:
    - prepare the soil or substrate for planting;
    - obtain the soil or substrate at its field capacity;
    - treat the soil or substrate at field capacity of the previous stage with ozonated water containing min. 2 ppm of ozone, where ozonated water is prepared in situ with an ozone production equipment connected to the water supply with a pH between 5.0 and 8.5; 25
    - leave between 30 min and 24 hours after the ozone treatment;
    - inoculate the disinfected soil or agricultural substrate with at least one kind of beneficial microorganism; Y
    - Plant the vegetable to be grown.
     30
    The stage of preparation of the soil or substrate for planting may include carrying out the decompaction and formation of ridges or plateaus, installing the irrigation network and, if necessary, installing the padding if necessary.

    Preferably, the treatment with ozonized water included in the method of disinfection of soils or other substrates for agricultural cultivation described in this patent application includes the application, by means of the irrigation network in the disinfected bulb, of beneficial microorganisms that re-colonize the cultivation soil and prevent recolonization by pathogens. 5

    Planting can be done with the usual systems, including the placement of tunnels or quilts that are required for normal crop development.

    The method of the present invention has proven effective in disinfecting soils against 10 phytopathogenic fungi such as, for example, Sclerotinia sp, Fusarium oxysporium and Phytophthora citrophthora. In particular, 100% disinfection against the phytopathogenic fungi mentioned above was obtained in tests

    Additionally, this method of disinfection is also effective against populations of 15 pathogenic mesophilic bacteria such as, for example, Erwinia amylovora and Claribacter michiganensis. In the tests carried out with respect to these bacteria, a mortality of less than 50% was obtained after a first application of ozonized water. Subsequently, after a second application, a reduction of at least 50% was maintained.
     twenty
    As a result of the reduction of the populations of microorganisms that is achieved with the disinfection method of the present invention, an increase in the vegetative development of the plants grown in said soil or substrate is achieved.

    Thus, the method of the present invention allows ozone to be used as a soil disinfectant or substrate, since it allows to effectively generate the necessary amount of ozone in the place and time it is required. Therefore, this method provides a viable alternative to the disinfection of agricultural soils, as a previous step to the implantation of the crop, avoiding the use of phytosanitary ware, the contamination and the accumulation of residues in soil and plant. This is due to the fact that ozone has a great oxidizing power, eliminating all 30 microorganisms and that the release of oxygen radicals in large quantities eliminates the microbiota from the soil.

    Alternatively, the method described in this patent application can be applied to soils or other substrates with cultivation in production, both of vegetables and fruit trees. In these cases, the method preferably comprises the following steps:
    - obtain the soil or substrate at its field capacity;
    - treat the soil or substrate of the previous stage with ozonated water containing min. 2 ppm 5 of ozone, where ozonated water is prepared in situ with an ozone production equipment connected to the water supply with a pH between 5.0 and 8.5;
    - leave between 30 min and 24 hours after the ozone treatment;
    - inoculate the soil or agricultural substrate disinfected with at least one kind of beneficial microorganism. 10

    The method described in this patent application allows to disinfect soils or other agricultural cultivation substrates instantly, without leaving harmful residues since the only by-product resulting from the degradation of ozone in the soil is oxygen, which is very beneficial for root development and implantation of beneficial microorganisms. fifteen

    Both in the use of chemical disinfections and in Solarization techniques, the waiting time after the necessary disinfection for it to be effective is between 20 and 60 days. Advantageously, the method of disinfection of the present invention allows the disinfection of the soil with the implanted culture, that is, it allows the application of ozone to the soil or substrate infested with pathogens and with the cultivation and production, without leaving any type of Toxic residue or that can be recorded in the analysis of the product collected. Inoculation between 30 minutes and 24 hours of beneficial microorganisms will be responsible for regenerating the affected root system.
     25
    It is also advantageous that, in the event of a high infection of pathogens during cultivation, the method of the present invention can be performed several times, since no waste is generated, nor does it adversely affect the vegetation. Likewise, it is also possible to carry out several treatments with ozone (several applications of ozone) before proceeding to inoculation with the beneficial microorganisms. 30

    Additionally, the disinfection method described in this patent application is highly versatile, since it can be applied before or after planting, after performing a chemical disinfection by another known method or without having performed any previous disinfection. 35

    BRIEF DESCRIPTION OF THE FIGURES

    Figure 1: Diagram showing the effect of water with ozone on various fungi.
     5
    Figure 2a: Image showing the containers with substrate used in example 1.

    Figure 2b: Image showing the system used in example 1 to perform the disinfection of a substrate according to the method of the present invention.
     10
    Figure 3a: Graph showing the survival of phytopathogenic fungi after application 1 of Example 1. The amount of fungi present in the substrate is analyzed at zero time (t = 0) and 24 hours after application (t = 1), a 20 cm, 40 cm and 60 cm deep.

    Figure 3b: Graph showing the survival of phytopathogenic bacteria after application 1 15 of example 1. The amount of bacteria present in the substrate is analyzed at zero time (t = 0) and 24 hours after application (t = 1), at 20 cm, 40 cm and 60 cm deep.

    Figure 4a: Graph showing the survival of phytopathogenic fungi after application 2 of Example 1. The amount of fungi present in the substrate at zero time (t = 0), 20 1 day (t = 1) and 30 days (t = 30) after application, at 20 cm, 40 cm and 60 cm deep.

    Figure 4b: Graph showing the survival of phytopathogenic bacteria after application 2 of Example 1. The amount of fungi present in the substrate is analyzed at zero time (t = 0), 25 1 day (t = 1) and 30 days (t = 30) after application, at 20 cm, 40 cm and 60 cm deep.

    Figure 5: Image showing the state of tomato plants after the first application of example 1: Fig. 5a: control; Fig. 5b: ozone treatment. 30

    Figure 6: Image showing the state of tomato plants after the second application of Example 1. Fig. 6a: control; Fig. 6b: ozone treatment.

    Figure 7: Sampling points collected in example 3 35

    Figure 8: Images showing: (A) soil sample under the magnifying glass; (B), (C) and (D) detail nematodes.

    Figure 9: Graph showing the evolution of the nematode population in the soil after treatment with ozone and after the inoculation of microorganisms obtained in example 5.

    Examples

    Example 1: Efficacy of ozone treatment in disinfection of uncultivated soils 10

    The general objective of the study was to evaluate the effectiveness of the use of ozone as a strategy in soil disinfection. In particular, it was intended to study the effect of the disinfection method on tomato plants, and relate the oxidative power of ozone with the elimination of pathogens at different depths. fifteen

    To achieve the objectives mentioned above, uncultivated soil was infected with the phytopathogenic species Sclerotinia, Fusarium, Erwinia, Phytophthora and Clavibacter. The trial was conducted in Lorca (Murcia). It took place outdoors in buckets with uncultivated soil and where tomato, pepper and melon had previously been grown. After carrying out the first application of the method of the present invention, tomato plants, Lycopersicum esculentum, were transplanted, evaluating the response of the plant to the treatments.

    The treatments tested were: T0 (control) and T1 (ozone). After the application of method 25 twice in a row, the following beneficial microorganisms were inoculated (mixture called "formulated from microorganisms (1)"): Trichodermas (4x108 CFU), Bacillus (1.5x108 CFU), Azotobacter (1, 5x108 CFU) and Pseudomonas (1.5x108 CFU).
     30
    The microbiological content of the soil was evaluated at different depths: 20, 40 and 60 cm., Before and after applications.

    1.1 Test protocol
    Containers of a known volume of 1000 l (1x1x1 m) were installed in the field. On the other hand, the substrate from the greenhouse was selected and homogenized with previous cultivation of melon, pepper and tomato. Subsequently, the containers were filled with this substrate.

    In the laboratory, the species of: 5 were cultured in vitro
     Phytopathogenic bacteria: Erwinia amylovora and Clavibacter michiganensis
     Phytopathogenic fungi: Sclerotinia sp, Fusarium oxysporium and Phytophthora citrophthora

    Each microorganism was grown in liquid medium to reach a concentration of 108 10 cfu / ml. For each of the cuvettes, 1 liter of microbial solution was prepared.

    The pathogenic microorganisms were then inoculated into the substrate, periodic waterings were made until the substrate capacity was reached, samples were taken at different depths (20 cm, 40 cm and 60 cm) and the phytopathogen count was performed on said 15 samples, to verify the permanence and presence of phytopathogens in the soil.

    A first application of the ozone disinfection method was performed. For this, the ozonation equipment was inserted into the irrigation system and the parameters of said equipment were adjusted to achieve ozonized water with min. 2 ppm dissolved ozone. Subsequently, the soil was left at rest for 30 min and tomato plants, Lycopersicum esculentum, were transplanted. Subsequently, a second application of the ozone disinfection method was carried out under the same conditions indicated above and, after allowing the treated soil to stand for 30 min, the microorganism formulation was inoculated (1).
     25
    Figure 2a shows the placement of containers in the field, while figure 2b shows the assembly made to insert the ozonation equipment used to the irrigation system.

    To analyze the effect of the treatment on soil disinfection, samples were taken at 30 different depths (20 cm, 40 cm and 60 cm) and on different dates, and the microbial load in each of the samples was analyzed.

    After as mentioned above, once the first disinfection was finished, tomato seedlings were transplanted into the buckets to assess the "residual effect" of the treatment. Subsequently, the study of the vegetative development of the plants was carried out.

    1.2 Treatments 5

    The treatments, applications and sampling are referred to in the following table:

    Table 1: Treatments
     10
    After the first application of the disinfection method, on September 19, 2014, 2 tomato plants were transplanted per container. The residual effect of ozone was evaluated.

    1.3 Experimental size and design
     fifteen
    The control treatment corresponds to container No. 1. Since there is only one repetition, 3 subsamples were taken during sampling.

    Table 2: Sketch of the experimental design
     twenty
    1.4 Parameters evaluated

    During the course of the trial, the parameters evaluated were:
    - Flow and ppm ozone at the exit.
    - Soil microbiota evaluation (t = 0; t = 7 days and t = 30 days). 25
    - Relationship of depth with the possible fungicidal effect.
    - Once the tomato plants were established, it was evaluated whether the treatments caused phytotoxicity. The parameters that will be observed in the culture will be the appearance of necrosis and burns in leaves and fruits.
    - Vegetative development of the crop.
     5
    The effect of the treatments (ozone, control) and their evaluation was determined by the Student test in the SPSS statistical package. The test determines whether the means that the experiments show are significantly different with a level of reliability (P> 0.05). The results are represented by bar diagrams, the results tables show if there were significant differences (different letter) or if there is no evidence of 10 differences between treatments (same letter).

    1.5. Results

    1.5.1 Flow and Flow and ppm ozone at exit 15

    During the first application, the collected data is shown in the following table:

     Time (minutes)  Equipment involved Description / Observations
     0-120  Water Saturation Irrigation
     15-20  Ozone equipment 4-time analysis test to determine the grams of ozone per liter of water. 2 ppm Minimum level for good disinfection
     Drip irrigation
     fifteen  Reading 2 ppm
     55  Reading 2.3 ppm
     65  Reading 2.89 ppm
     115  Reading 4.49 ppm at direct pump output
     3.92 ppm in the dropper
    Table 3: Ozone readings
     twenty
    1.5.2. Evaluation of the microbial population after Application 1
    This section describes the data obtained. As explained in the test protocol, soil samples were taken at different depths (20 cm, 40 cm and 60 cm) and quality controls were performed quantifying the number of fungi and pathogenic bacteria.

    A. Pathogenic fungi 5

    Prior to the incorporation of the treatments and 24 hours after the application, the survival of pathogenic fungi was evaluated. Analyzed the data by treatment (see Figure 3a), we found that:
     10
    - In the control treatment: the microbial load was similar before and after at all depths tested, except 40 cm, where a wash occurred.

    - The application of ozone meant a reduction of 100% at 20 and 60 cm deep.
     fifteen
    B. Pathogenic bacteria

    At each of the depths tested (20cm, 40cm and 60cm), both treatments reduced the populations of bacteria present in the soil (see figure 3b). At all depths evaluated (except 60 cm), the populations of pathogenic bacteria were 20 lower than the control, this decrease being less than 50%.

    1.5.3. Evaluation of the microbial population after Application 2

    A. Pathogenic fungi 25

    As shown in Figure 4a, the application of ozone reduced pathogenic fungi by 100% to a depth of 40 and 60 cm, maintaining the effectiveness of both products and extending the effect for 30 days At a depth of 20 cm, the Ozone treatment reduced the population by 100%, with traces of fungi appearing 30 months later, possibly due to soil contamination due to environmental factors.

    B. Pathogenic bacteria

    The study of the data (see figure 4b) shows the disinfectant power of ozone, although the reduction was not total. Given the speed of reproduction of the bacteria, it is estimated that after the residual effect of the products disappears completely, populations similar to the control will be reached.
     5
    1.6. Phytotoxicity in tomato plants

    After the first application of the ozone treatment, 2 tomato plants were transplanted in each of the containers. The growth of the plants was evaluated for three months, ending the analysis of this parameter on January 2 due to frost in the area (see figures 5a and 5b).

    The growth in plants where the ozone treatment had been applied, showed a vigorous vegetative development, due to the decrease of pathogenic microorganisms; while in control plants, its development was medium-low. Two weeks after the second application, the control plants died of the infection (see figures 6a and 6b).

    1.7. Conclusions

    The results obtained showed that the level of ozone disinfection was 20 100% compared to the phytopathogenic fungi tested. Additionally, populations of pathogenic mesophilic bacteria decreased in number after application of the disinfectant, with a mortality of less than 50% after the first application. During the second application,
    the reduction of 50% was maintained, with the exception of what was observed at a depth of 60 cm, where the reduction reached 60%. 25

    In addition, in the samples treated with ozone, the vegetative development of tomato plants was vigorous due to the reduction of populations of microorganisms., While in tomato plants grown in control containers they showed low-medium growth and ended up dying due to infection of pathogens. 30

    As a complement, after the first application tomato plants were transplanted in each of the repetitions and it was evaluated whether the application of ozone caused phytotoxicity. Three months after the transplant, ozone-treated plants showed growth and
    normal vegetative development, while the control plants died as a result of the attack of pathogens present in the soil.

    Example 2: Disinfection of nematodes in pepper var. census
     5
    The test is carried out in a Padrón Peppers farm in May 2015 that presents a high degree of nematode involvement and the property intends to start the plantation because production is already lost. On an area of 500 m2 of greenhouse, with a water consumption of 3000 l / h, ozone disinfection is carried out at a dose of 6 ppm, checking with the REDOX readings that in the drip emitters plus 10 remote a 1000 mV reading, based on a value in the 185 mV ozone-free irrigation water.

    At the end of the treatment, the inoculation of the microorganism formula (1) is performed (see example 1). Seven days after the treatment, soil samples are taken to see the level of nematode infestation, observing a 90% decrease in the population.

    In particular, after disinfection through ozonized irrigation in cultivation of Padron pepper affected by nematodes (Meloidogyne) in full production, the following 20 results were obtained:

    - Analytics prior to disinfection: Meloidogyne sp. 88 juveniles / 100 cc soil
    - Post-disinfection analytics: Meloidogyne sp. 8 juveniles / 1 cc soil.
     25
    The treated part of the farm recovered from the damage and continued in production until the date scheduled for its start.

    Example 3: Disinfection of nematodes in citrus cultivation (lemon trees). Effect of ozonation and inoculation with beneficial microorganisms in the control of 30 phytopathogenic soil nematodes

    This citrus test was carried out on a plot with a high rate of nematode infection, during the months of May and September 2015. The effect of two ozone applications and a final application of a mixture of microorganisms was evaluated (formulated 35
    of microorganisms (2)) formed by: Bacillus (1.5x108 CFU), Azotobacter (1.5x108 CFU) and Pseudomonas (1.5x108 CFU).

    The parameters studied were: evolution of the population of phytopathogenic nematodes, evolution of the fungal population and after the application of the formulation of microorganisms (2), 5 a count of the number of bacteria in soil was made. The results showed that the application of ozone along with beneficial microorganisms significantly reduced the population of phytopathogenic nematodes in soil.

    The objective of this trial was to evaluate the action of ozone and beneficial microorganisms in the control of phytopathogenic nematodes in citrus fruits.

    3.1. Material and methods

    On a plot with high infection by nematodes of the genus Pratylenchus sp, 4 repetitions were selected. Figure 7 shows the collected sampling points.

    The date of application of the products was:
    - Ozone: applied at a concentration of 5-6 ppm. Applications: May 21 and 27.
    - Formulated from microorganisms (2) (Bionema Plus): A single application of a dose of 20 20 l / ha took place on June 4.

    Table 1 Sampling

    3.2. Conclusions 25

    The results have shown that the application of ozone and the formulation of microorganisms (2) significantly reduced the population of phytopathogenic nematodes, decreasing from 50 nem / g to 0.2 nem / g, a population practically non-existent.
     30
    Example 4: Evolution of nematodes in the soil after treatment with ozone and inoculation of microorganisms

    This test was performed in T.M. Benifaió (Valencia), in clay-loam. The treatments were carried out at the end of a vegetable crop, before carrying out the new planting of cucumbers, tomatoes, peppers.

    The land stood out for its high content of nematode infection, severely affecting crop production.
     10
    The method for soil disinfection described in this patent application was applied, where the treatment with ozonated irrigation water (5.5 ppm ozone) was carried out for 2 hours, and the inoculation took place through the application of the formulation of microorganisms (1) (see example 1) colonizers 24 hours after ozone disinfection. fifteen

    As can be seen in Figure 9, before applying the treatment, the sample of soil extracted had 480 juveniles / 100 cc of soil. After carrying out the ozone treatment, the presence of juveniles was reduced to 44/100 cc of soil and 15 days after inoculation with the formula of microorganisms (1), the analyzed sample 20 presented 1 juvenile / 100 cc of soil.

    These results show a considerable decrease in the percentage of nematodes. Also, you can also see an increase in the amount of Saprophytes in 20 units / 100 cc land. 25

    The different tests carried out show that, both in bare soils and in fields with crops in production, the best results are obtained by combining the punctual treatment with ozone (min. 2 ppm) in irrigation water, followed by inoculation with beneficial microorganisms. 30
    权利要求:
    Claims (7)
    [1]

    1.- A method to disinfect soils or other substrates of agricultural cultivation, characterized in that it comprises:
    - obtain a soil or other agricultural crop substrate at its field capacity; 5
    - treat the soil or substrate at field capacity of the previous stage with ozonated water containing min. 2 ppm of ozone, where ozonated water is prepared in situ with an ozone production equipment connected to the water supply with a pH between 5.0 and 8.5;
    - leave between 30 min and 24 hours after the ozone treatment; and
    - inoculate the soil or agricultural substrate disinfected with at least one species of beneficial microorganism.

    [2]
    2. The method for disinfecting according to claim 1, wherein the ozone content dissolved in the ozonated water is between 5 and 6 ppm.
     fifteen
    [3]
    3. The method for disinfecting according to any one of claims 1 to 2, wherein the treatment with ozonized water is carried out for a period of time between 1 h 30 min and 2 hours.

    [4]
    4. The method for disinfecting according to any one of claims 1 to 3, wherein the beneficial microorganism is selected from the group consisting of Trichodermas, Bacillus, Azotobacter, Pseudomonas and any combination of the foregoing.

    [5]
    5. The method for disinfecting according to any one of claims 1 to 4, wherein the water is applied by localized irrigation. 25

    [6]
    6. The method for disinfecting according to any one of claims 1 to 5, wherein the soil or substrate has no crop in production, and the method comprises the following steps:
    - prepare the soil or substrate for planting; 30
    - obtain the soil or substrate at its field capacity;
    - treat the soil or substrate at field capacity of the previous stage with ozonated water containing min. 2 ppm of ozone, where ozonated water is prepared in situ with an ozone production equipment connected to the water supply with a pH between 5.0 and 8.5;
    - leave between 30 min and 24 hours after the ozone treatment; 35
    - inoculate the disinfected soil or agricultural substrate with at least one kind of beneficial microorganism; Y
    - Plant the vegetable to be grown.

    [7]
    7. The method for disinfecting according to any one of claims 1 to 5, wherein the soil or substrate with crop in production, and the method comprises the following steps:
    - obtain the soil or substrate at its field capacity;
    - treat the soil or substrate of the previous stage with ozonated water containing min. 2 ppm of ozone, where ozonated water is prepared in situ with an ozone production equipment connected to the water supply with a pH between 5.0 and 8.5; 10
    - leave between 30 min and 24 hours after the ozone treatment; and
    - inoculate the soil or agricultural substrate disinfected with at least one kind of beneficial microorganism.
     fifteen
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    同族专利:
    公开号 | 公开日
    PL3192371T3|2019-09-30|
    EP3192371B1|2019-02-27|
    ES2717528T3|2019-06-21|
    ES2625034B1|2018-05-04|
    CA2954649A1|2017-07-18|
    TR201904594T4|2019-04-22|
    MA43286B1|2019-05-31|
    MA43286A|2017-07-19|
    EP3192371A1|2017-07-19|
    PT3192371T|2019-04-23|
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    优先权:
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    ES201630043A|ES2625034B1|2016-01-18|2016-01-18|METHOD FOR DISINFECTION OF AGRICULTURAL SOILS|ES201630043A| ES2625034B1|2016-01-18|2016-01-18|METHOD FOR DISINFECTION OF AGRICULTURAL SOILS|
    TR2019/04594T| TR201904594T4|2016-01-18|2017-01-02|method for disinfection of agricultural soil.|
    PL17150031T| PL3192371T3|2016-01-18|2017-01-02|Method for disinfection of agricultural soil|
    EP17150031.7A| EP3192371B1|2016-01-18|2017-01-02|Method for disinfection of agricultural soil|
    ES17150031T| ES2717528T3|2016-01-18|2017-01-02|Method for the disinfection of agricultural soils|
    PT17150031T| PT3192371T|2016-01-18|2017-01-02|Method for disinfection of agricultural soil|
    MA43286A| MA43286B1|2016-01-18|2017-01-02|Method for disinfecting agricultural soils|
    CA2954649A| CA2954649A1|2016-01-18|2017-01-13|Method for disinfection of agricultural soil|
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