<sup2 / > ? <sub2 / > ?0? ?FERTILIZER COMPOSITION CONTAINING ELEMENTAL SULFUR AND TRIGONELLINE AS A POTENTIOMETER OF MICROBIOLOGICAL OXIDATION OF S

Abstract

The present invention provides a fertiliser composition comprising trigonelline as an enhancer of the microbiological oxidation of elemental sulphur to sulphate ion (S0 to SO42-) where trigonelline increases SO42- levels in agricultural soils.

Description

[0001] The present invention relates to a fertiliser composition including an enhancer of the microbiological oxidation of elemental sulphur (S 0< ), as well as to the use of said fertiliser composition.

[0002] More specifically, in a first aspect, the invention provides a fertiliser composition that includes trigonelline as an enhancer of the microbiological oxidation of elemental sulphur (S 0< ), wherein trigonelline increases the rate of SO 4 2-< generation in the presence of S 0< , the application thereof constituting a source of sulphur for the microbiological release of sulphuric acid in agricultural soils and an alternative to conventional sulphur fertilisers and amendments.

[0003] In a second aspect, the invention relates to a combination of the described fertiliser composition together with an additional fertiliser and / or biostimulant.

[0004] Sulphur (S) is an essential element for plants as it forms part of the cysteine and methionine amino acids, determining the structural conformation of proteins and the binding thereof to metal ligands (Ceccotti SP. 1996. Plant nutrient sulphur - A review of nutrient balance, environmental impact and fertilizers. Fertilizer Research 43(1):117-125). In addition, sulphur forms part of numerous vitamins, such as biotin and thiamine, and of essential cofactors, such as in coenzyme A.

[0005] The most common inorganic form in which sulphur is found in well-drained soils is as sulphate (SO 4 2-< ), and this is the form in which it is preferentially taken up by plants, although it can also be assimilated in the form of thiosulphate (S 2 O 3 2-< ). However, inorganic forms of sulphur usually constitute less than 5% of the total sulphur present in agricultural soils, while the majority (> 95% of total sulphur) is bound to organic molecules in organic matter of the soil or microbial biomass, and is therefore generally not directly available for assimilation by the plant.

[0006] Furthermore, an increasing sulphur deficiency in agricultural soils has been observed over the last 50 years due to several factors, mainly including: reduced sulphur emissions from industrial sources, the use of sulphur-free mineral fertilisers, decreased use of organic fertilisers and high sulphur extraction from soils by highyielding plant varieties in relation to intensive agricultural practices (Etienne et al., 2018. Assessment of Sulfur Deficiency under Field Conditions by Single Measurements of Sulfur, Chloride and Phosphorus in Mature Leaves. Plants (Basel). 7(2)).

[0007] Likewise, the SO 4 2-< ion, although it has a higher adsorption affinity to soil colloids than NO 3 -< or Cl -< ions, is subject to leaching losses, which contributes to aquifer contamination. In tropical soils, sulphur deficiency often occurs naturally due to high mineralisation rates of organic forms (Ribeiro et al., 2001. Dynamics of Sulfur Fractions in Brazilian Soils Submitted to Consecutive Harvests of Sorghum. Published in Soil Sci. Soc. Am. J. 65:787-794).

[0008] The application of elemental sulphur (S 0< ) as a fertiliser is an economical alternative for sulphur replenishment in agricultural soils and allows the use of concentrated commercial formulations of other nutrients, such as nitrogen or potassium. The oxidation of elemental sulphur (S 0< ) to sulphate (SO 4 2-< ) is gradual, thus reducing SO 4 2-< losses by leaching, and depends on microbial activity and diversity of the soil, as well as environmental conditions (soil pH, temperature or humidity) (Tourna et al., 2014. Links between sulphur oxidation and sulphur-oxidising bacteria abundance and diversity in soil microcosms based on soxB functional gene analysis. FEMS Microbiol Ecol. 88:538-49). The transformation of S° to SO 4 2-< is also influenced by the particle size of the S 0< , with oxidation being faster the smaller the particle size.

[0009] Furthermore, it is known that enzymatic oxidation of S 0< to SO 4 2-< by certain bacteria and archaea under aerobic conditions produces sulphuric acid (Wainwright, 1978. Microbial sulphur oxidation in soil. Sci. Prog. (Oxford). 65: 459-475; Fike et al., 2016. Geomicrobiology of Sulfur, in Ehrlich's Geomicrobiology, 6th Edn. Eds H.L. Ehrlich, D.K. Newman, and A. Kappler (Boca Raton, FL: Taylor & Francis), 479-515):         S 0< + 1.5O 2 + H 2 O → H 2 SO 4

[0010] The microbiological release of sulphuric acid contributes to the solubilisation of certain plant nutrients that are in insoluble forms. An example is the phosphorus present in phosphate rock, the availability of which to plants can be greatly increased by being solubilised by micro-organisms of the soil when applied together with elemental sulphur (Lipman et al., 1916. Sulfur oxidation in soils and its effect on the availability of mineral phosphates. Soil Science: 2: 499-538; Evans et al., 2006. Application of reactive phosphate rock and sulphur fertilisers to enhance the availability of soil phosphate in organic farming. Nutrient Cycling in Agroecosystems 75:233-246).

[0011] Within the bacterial domain, the main genera involved in elemental sulphur oxidation in agricultural soils are Acidithiobacillus, Acidianus, Alicyclobacillus, Aquaspirillum, Bacillus, Beggiatoa, Mesorhizobium, Methylobacterium, Parococcus, Pseudomonas, Rhizobium, Starkeya, Thermithiobacillus, Thermothrix, Thiobacillus, Xanthobacter. However, in the application of elemental sulphur (S 0< ) it must be considered that it must be transformed to sulphate ion (SO 4 2-< ) in a short enough period of time to cover the agronomic needs in one crop cycle.

[0012] In this regard, some solutions have been proposed to increase the rate of sulphur oxidation. For example, patent application WO 2016 / 126278 describes an enhanced sulphate release fertiliser composition consisting of a mixture of elemental sulphur and humic acids.

[0013] Although the oxidation of elemental sulphur to sulphate ion is accelerated in this document, the rate of this oxidation reaches its maximum after 6 weeks, until the maximum amount of sulphur is released under controlled conditions of temperature and humidity, not being high enough for adequate agronomic efficiency in view of the fact that, under real environmental conditions (with wide fluctuations in temperature and humidity between day and night or depending on climatic phenomena) and in certain soils, such as calcareous soils, the release of sulphur can slow down considerably.

[0014] Cifuentes and Lindeman (in "Organic matter stimulation of elemental sulfur oxidation in a calcareous soil", Soil Sci. Soc. Am. J. 57: 727-731, 1993) show that the incorporation of different sources of organic matter (glucose, starch, cellulose or straw) into a soil promotes the oxidation of elemental sulfur. This increased oxidation of S 0< in the presence of organic molecules seems to be due to an increased activity of chemoheterotrophic and mixotrophic bacteria capable of oxidising S 0< (Bharathi, 2008. Sulfur cycle. Encyclopedia of ecology. Academic press. 3424-3431).

[0015] In fact, it is known that certain organic molecules, present for example in crop root exudates, have the ability to specifically modulate the growth or activity of bacteria that regulate nutrient cycles in agricultural soils, including sulphur, and have beneficial effects on crop nutrition (Meena et al., 2016, Potassium Solubilizing Microorganisms for Sustainable Agriculture, Free Review, Ed. Springer India; Zhalnina et al 2018, Dynamic root exudate chemistry and microbial substrate preferences drive patterns in rhizosphere microbial community assembly, Nat Microbiol, 3(4):470-480; Lamers et al., 2012, Microbial Transformations of Nitrogen, Sulfur, and Iron Dictate Vegetation Composition in Wetlands: A Review. Front Microbiol. 3: 156; Grayston and Germida, 1990, Influence of crop rhizospheres on populations and activity of heterotrophic sulfur-oxidizing microorganisms. Soil Biol. Biochem. 22: 457-463).

[0016] For the above reasons, in the field of plant nutrition there is currently a need to look for alternatives to conventional sulphur fertilisers that make it possible to provide sulphur in an economical, efficient and sustainable way and to promote the microbiological production of sulphuric acid to increase the solubilisation of plant nutrients in agricultural soils.

[0017] Considering the above, the present invention is based on the above-mentioned approaches in such a way that, by regulating the sulphur transformation processes in soils, certain organic molecules can, in the presence of elemental sulphur, increase the availability of this nutrient for plants and favour the microbiological release of sulphuric acid in agricultural soils. This approach would also constitute an alternative to conventional sulphur fertilisers and amendments.

[0018] Thus, in a first aspect, the present invention provides a fertiliser composition that includes trigonelline as an enhancer of the microbiological oxidation of elemental sulphur to sulphate ion (S 0< to SO 4 2-< ) wherein trigonelline increases the levels of SO 4 2-< in agricultural soils.

[0019] Trigonelline, or N-methylnicotinic acid, is an alkaloid found in many plants, such as pea, hemp, oats, potato and fenugreek, in which it has various regulatory functions (Garg, 2016, in Nutraceuticals Efficacy, Safety and Toxicity, pp. 599-617). Trigonelline is the methylation product of niacin (vitamin B3).

[0020] As mentioned above, in a first aspect, the present invention provides a fertiliser composition that includes elemental sulphur (S 0< ) and trigonelline as an enhancer of the microbiological oxidation of S 0< .

[0021] In view of the examples described hereafter, the generation of SO 4 2-< in trigonelline-treated soil depends on the presence of S 0< and is mediated by soil micro-organisms. Without being bound by any particular theory, the present inventors believe that, in the presence of S 0< , trigonelline stimulates the sulphur-oxidising bacteria present in the soil resulting in increased oxidation of S 0< . As previously discussed, the addition of various organic matter stimulates S 0< oxidation; however, the nature of the organic matter has an important influence on this process. The stimulation of S 0< oxidation by the application of trigonelline is greater than that of other organic matter, such as humic acids or glucose, which have a proven effect on S 0< oxidation. Moreover, as demonstrated in the different examples, trigonelline has a stronger effect on S 0< oxidation than other organic molecules chosen among organic acids, amino acids, alkaloids, sugars and alcohols, which are organic metabolites with the potential to have an inducing effect on soil microorganisms. More specifically, the effect of trigonelline is probably mediated by heterotrophic and mixotrophic micro-organisms capable of oxidising S 0< , since it is known that the addition of organic matter stimulates chemoheterotrophic micro-organisms and not chemoautotrophic microorganisms.

[0022] In one embodiment, the fertiliser composition of the invention is in powder form and comprises between 85 and 99.5% by weight of S 0< and between 0.5 and 15% of trigonelline.

[0023] In another embodiment, the fertiliser composition of the invention comprises between 85 and 99.5% by weight of S 0< , between 0.5 and 10% by weight of trigonelline and between 0.5 and 5% by weight of other components selected from the group consisting of sugars, amino acids, organic acids, polyamines, alcohols, nucleotides and combinations thereof, the fertiliser composition being in the form of a watersoluble powder.

[0024] In this embodiment, the presence of the other components included in the fertiliser composition of the invention is due to the fact that the presence of organic molecules favours the oxidation of inorganic sulphur (Cifuentes and Lindemann, 1993; Bharathi, 2008). Therefore, the presence of these components other than trigonelline and elemental sulphur in the composition of the invention is based on the fact that such components are organic molecules that can act as a source of energy or activate the metabolism of certain microorganisms.

[0025] When present in the present fertiliser composition, sugars are preferably selected from mono- and di-saccharides such as sucrose, fructose, trehalose, glucose, arabinose, maltose, lactose, as well as mixtures thereof.

[0026] When present in the present fertiliser composition, amino acids are preferably selected from threonine, lysine, phenylalanine, methionine, GABA, ornithine, glycine, aspartic acid, glutamine, glutamic acid, serine, asparagine, tyrosine, tryptophan, valine, leucine, isoleucine, proline, 4-hydroxyproline, arginine, histidine, alanine, cysteine, and mixtures thereof.

[0027] When present in the present fertiliser composition, the organic acids are preferably selected from lactic acid, succinic acid, oxalic acid, gluconic acid, threonic acid, citric acid, fumaric acid and mixtures thereof.

[0028] Polyamines, if present in the present composition, are preferably selected from putrescine, spermidine, spermine and mixtures thereof.

[0029] When present in the fertiliser composition, alcohols are preferably selected from glycerol, sorbitol, mannitol, myoinositol, as well as mixtures thereof.

[0030] The fertiliser composition of the invention is formulated in powder form, as indicated above, but can also be formulated as an emulsion composition with the addition of water or in granulated form by means of the addition of granulating agents known to the person skilled in the art.

[0031] According to the second aspect, the invention relates to a fertiliser composition such as the one described above in combination with an additional fertiliser selected from nitrogen fertilisers, phosphate fertilisers, potassium fertilisers, calcium fertilisers and amendments, micronutrients, boric acid, leonardite and feldspar, as well as combinations thereof, and / or in combination with one or more biostimulants selected from the group consisting of amino acid hydrolysates, humic extracts, seaweed extracts, live micro-organisms, extracts of micro-organisms and combinations thereof. The live micro-organisms or extracts of micro-organisms shall preferably be of the species Pichia guilliermondii, Azotobacter chroococcum, Bacillus megaterium, or other bacteria belonging to genera recognised for their elemental sulphur oxidising capacity, preferably Acidithiobacillus, Acidianus, Alicyclobacillus, Aquaspirillum, Bacillus, Beggiatoa, Mesorhizobium, Methylobacterium, Parococcus, Pseudomonas, Rhizobium, Starkeya, Thermithiobacillus, Thermothrix, Thiobacillus, Xanthobacter.

[0032] In this case, the composition of the invention is present in the combination in a proportion of 10 to 60% by weight.

[0033] In one embodiment, the additional nitrogen fertiliser is present in the blend in a proportion of 5 to 90 % by weight and is selected from urea, potassium nitrate, ammonium nitrate, calcium nitrate, calcium ammonium nitrate, nitromagnesium.

[0034] In another embodiment, the additional phosphate fertiliser is present in the combination in a proportion of 5 to 90 % by weight and is selected from phosphate rock, triple superphosphate, single superphosphate, concentrated superphosphate, phosphoric acid.

[0035] In yet another embodiment, the additional potassium fertiliser is present in the blend in a proportion of 5 to 90% by weight and is selected from potassium chloride and potassium hydroxide.

[0036] In another embodiment, the additional calcium fertiliser is present in the blend in a proportion of 5 to 90% by weight and is selected from calcium chloride, calcium cyanamide, dolomite, limestone, calcium oxide, calcium hydroxide.

[0037] In yet another embodiment, the additional micronutrient fertiliser is present in the combination in a proportion of 1 to 30% by weight and is selected from ammonium molybdate, cobalt chloride and micronutrients (iron, magnesium, zinc, manganese, copper) combined with complexing agents (humates, citrate, gluconates, heptagluconates and amino acids) or with chelating agents (ethylenediaminetetraacetic acid EDTA, ethylenediamine-di(o-hydroxyphenyl acetic acid) EDDHA, diethylenetriaminepentaacetic acid DPTA).

[0038] In a further embodiment, boric acid as an additional fertiliser is present in the combination in a proportion of 1 to 30% by weight.

[0039] In another embodiment, leonardite as an additional fertiliser is present in the combination in a proportion of 5 to 90% by weight.

[0040] In a further embodiment, feldspar as an additional fertiliser is present in the combination in a proportion of 5 to 90% by weight.

[0041] In the case of the combination of the fertiliser composition of the invention with biostimulants as described above, preferably the biostimulants are present in the combination in a proportion of 5 to 90% by weight.

[0042] It is also an object of the invention to use the fertiliser compositions described herein in powder form, in granulated form or in emulsion form.

[0043] In case of use of the composition of the invention in powder or emulsion form, it is preferably applied in an amount of 0.5 to 20 kg / ha and 0.06 to 1 kg / ha respectively.

[0044] In case of use of the composition of the invention in combination with another additional fertiliser in granular form, preferably said combination is applied directly in an amount of 75 to 1,500 kg / ha.Examples 1. Screening for organic molecules that stimulate elemental sulphur oxidation in an agricultural soil.

[0045] In order to identify compounds that promote the oxidation of S 0< to SO 4 2-< in agricultural soils more efficiently than those described to date, the effect on S 0< oxidation of different organic molecules belonging to the groups of organic acids, amino acids, alkaloids, sugars and alcohols was studied. For this purpose, different products consisting of 97.5% of S 0< and 2.5% of the organic molecule to be tested are generated. Humic acids are used as a positive control, as it has been described that they increase the rate of sulphur oxidation. The different mixtures are incorporated into a soil at a rate of 3 g / kg soil. An agricultural soil with a sandy-loamy texture is used. The soil moisture is kept constant at 40% and the temperature at 20°C. Every 10 days a sample is collected and the amount of SO 4 2-< present in the soil is analysed.

[0046] The results of this test are shown in Table 1 below and in Figure 1. Table 1Days0102030405080Control -0.240.270.250.240.230.20.2S 0< 0.240.370.510.730.870.931.02S 0< +humic acids0.240.691.171.541.882.012.15S 0< +gluconic acid0.240.811.281.752.072.182.23S 0< +citric acid0.240.751.251.681.952.212.28S 0< +glutamic acid0.241.152.152.873.213.273.39S 0< +isoleucine0.241.092.012.753.123.283.49S 0< +leucine0.241.182.23.083.463.823.97S 0< +trigonellin e0.241.452.693.974.454.685.02S 0< +stachydrin0.240.410.680.891.051.091.12S 0< +glucose0.240.951.792.542.842.953.05S 0< +fructose0.240.891.562.072.352.582.88S 0< +glycerol0.240.681.031.431.762.132.65S 0< +mannitol0.240.761.251.761.972.122.19

[0047] The results indicate that trigonelline is the molecule that increases S 0< oxidation the most, multiplying the SO 4 2-< generated after 80 days by 2.3 with respect to humic acids.

[0048] Amino acids (leucine, isoleucine and glutamic acid), as well as glucose, fructose and glycerol also improve S 0< oxidation compared to humic acids. Gluconic acid, citric acid and mannitol show similar results to humic acids.2. Verification of the effect of trigonelline on S 0< oxidation and the mediation of soil micro-organisms

[0049] In order to prove that the effect of trigonelline depends on the presence of S 0< and that the oxidation of this elemental sulphur is mediated by microorganisms, on the one hand the generation of SO 4 2-< was studied in a soil treated with trigonelline and without S 0< , and on the other hand, the generation of SO 4 2-< in sterilised soils (free of microorganisms, Sueloest) to which S 0< and S 0< with trigonelline were applied. The soils were sterilised by fumigation with chloroform. The different mixtures were incorporated into a soil at a rate of 3 g / kg soil.

[0050] The results of this test are shown in Table 2 below and in Figure 2. Table 2Days0102030405080Control - (ground)0.240.270.250.240.230.20.2Trigonelline0.240.240.260.280.270.290.26S 0< 0.240.370.510.730.870.931.02S 0< +trigonelline0.241.452.693.974.454.685.02Soil ster + S 0< 0.240.230.230.270.250.280.26Soilster + S 0< +trigonelline0.240.250.240.280.290.30.31

[0051] The data obtained show that SO 4 2-< generation in trigonelline-treated soil depends on the presence of S 0< and is mediated by soil microorganisms.3. Study of combinations of the invention

[0052] The effect of the combination of trigonelline with other organic molecules, wherein Test 1 showed an increase in S 0< oxidation, was studied. For this purpose, three fertiliser compositions were prepared in powder form according to the invention with the following composition: A: 97.5% S 0< and 2.5% of the combination of between 30 and 80% by weight of trigonelline, between 5 and 30% of glutamic acid, between 5 and 30% of glucose and between 5 and 30% of gluconic acid. B: 97.5% S 0< and 2.5% of the combination of between 30 and 80% by weight of trigonelline, between 5 and 30% of leucine, between 5 and 30% of fructose and between 5 and 30% of citric acid. C: 97.5% S 0< and 2.5% of the combination of between 30 and 80% by weight of trigonelline, between 5 and 30% of isoleucine, between 5 and 30% of glycerol and between 5 and 30% of mannitol).

[0053] The results of this test are shown in Table 3 below and in Figure 3. Days0102030405080Control -0.240.270.250.240.230.20.2S 0< 0.240.370.510.730.870.931.02S 0< +humic acids0.240.691.171.541.882.012.15S 0< +trigonelline0.241.452.693.974.454.685.02A0,241.623.274.455.456.16.26B0.241.773.454.875.946.26.49C0.241.693.314.615.726.216.43

[0054] As can be seen from this test, all 3 combinations enhance the effect of S 0< +trigonelline application in a similar way, suggesting that the maximum microorganism-mediated S 0< oxidation capacity is achieved with the same.

Claims

1. A fertiliser composition including elemental sulphur (S0) and an enhancer of microbiological oxidation of S0 which is trigonelline.

2. The fertiliser composition according to claim 1, characterised in that it comprises between 85 and 99.5% by weight of S0 and between 0.5 and 15% of trigonelline.

3. The fertiliser composition according to claim 1, characterised in that it comprises between 85 and 99.5% by weight of S0, between 0.5 and 10% by weight of trigonelline and between 0.5 and 5% by weight of other components selected from the group consisting of sugars, amino acids, organic acids, polyamines, alcohols, nucleotides and combinations thereof, the fertiliser composition being in the form of powder.

4. The fertiliser composition according to claim 3, characterised in that the sugars are selected from mono- and di-saccharides, preferably sucrose, fructose, trehalose, glucose, arabinose, maltose, lactose, as well as mixtures thereof.

5. The fertiliser composition according to claim 3, characterised in that the amino acids are selected from threonine, lysine, phenylalanine, methionine, GABA, ornithine, glycine, asparagine, aspartic acid, glutamine, glutamic acid, serine, asparagine, tyrosine, tryptophan, valine, leucine, isoleucine, proline, 4-hydroxyproline, arginine, histidine, alanine, cysteine, and mixtures thereof.

6. The fertiliser composition according to claim 3, characterised in that the organic acids are selected from lactic acid, succinic acid, oxalic acid, gluconic acid, threonic acid, citric acid, fumaric acid and mixtures thereof.

7. The fertiliser composition according to claim 3, characterised in that the polyamines are selected from putrescine, spermidine, spermine and mixtures thereof.

8. The fertiliser composition according to claim 3, characterised in that the alcohols are selected from glycerol, sorbitol, mannitol, myoinositol, as well as mixtures thereof.

9. The fertiliser composition according to any of the preceding claims, characterised in that it is formulated in powder form.

10. The fertiliser composition according to any of claims 1 to 8, characterised in that it is formulated in the form of an emulsion in water.

11. The fertiliser composition according to any of claims 1 to 8, characterised in that it is formulated in granular form.

12. A combination of a fertilizer composition according to any of claims 1 to 11 and another additional fertilizer selected from nitrogen fertilizers, phosphate fertilizers, potassium fertilizers, calcium fertilizers and amendments, micronutrient fertilizers, boric acid, leonardite and feldspar, as well as combinations thereof, and / or in combination with one or more biostimulants selected from the group consisting of amino acid hydrolysates, humic extracts, algae extracts, live micro-organisms, extracts of micro-organisms and combinations thereof.

13. The combination according to claim 12, characterised in that the composition according to any of claims 1 to 11 is present in a proportion of 10 to 60% by weight.

14. The combination according to any of claims 12-13, characterised in that the additional nitrogen fertiliser is present in a proportion of 5 to 90% by weight and is selected from urea, potassium nitrate, ammonium nitrate, calcium nitrate, calcium ammonium nitrate, nitromagnesium.

15. The combination according to any of claims 12-13, characterised in that the additional phosphate fertiliser is present in a proportion of 5 to 90% by weight and is selected from phosphate rock, triple superphosphate, single superphosphate, concentrated superphosphate, phosphoric acid.

16. The combination according to any of claims 12-13, characterised in that the additional potassium fertiliser is present in a proportion of 5 to 90% by weight and is selected from potassium chloride and potassium hydroxide.

17. The combination according to any of claims 12-13, characterised in that the additional calcium fertiliser is present in a proportion of 5 to 90% by weight and is selected from calcium chloride, calcium cyanamide, dolomite, limestone, calcium oxide, calcium hydroxide.

18. The combination according to any of claims 12-13, characterised in that the additional micronutrient fertiliser is present in a proportion of 1 to 30% by weight and is selected from ammonium molybdate, cobalt chloride, micronutrients iron, magnesium, zinc, manganese and / or copper combined with the complexing agents humate, citrate, gluconate, heptagluconate and amino acids or with the chelating agents EDTA, EDDHA, DPTA.

19. The combination according to any of claims 12-13, characterised in that boric acid as an additional fertiliser is present in a proportion of 1 to 30% by weight.

20. The combination according to any of claims 12-13, characterised in that leonardite as an additional fertiliser is present in a proportion of 5 to 90% by weight.

21. The combination according to any of claims 12-13, characterised in that feldspar as an additional fertiliser is present in a proportion of 5 to 90% by weight.

22. The combination according to any of claims 12-13, characterised in that the live microorganisms or extracts of microorganisms are selected from the species Pichia guilliermondii, Azotobacter chroococcum, Bacillus megaterium, Acidithiobacillus, Acidianus, Alicyclobacillus, Aquaspirillum, Bacillus, Beggiatoa, Mesorhizobium, Methylobacterium, Parococcus, Pseudomonas, Rhizobium, Starkeya, Thermithiobacillus, Thermothrix, Thiobacillus, Xanthobacter and combinations thereof and are present in a proportion of 5 to 90% by weight.

23. A composition according to claim 9 for use in powder form characterised in that it is applied in an amount of 0.5 to 20 kg / ha.

24. The composition according to claim 10 for use in the form of an emulsion, characterised in that it is applied in an amount of 0.06 to 1 kg / ha.

25. A combination according to any of claims 12 to 22 for use thereof in granular form, characterised in that it is applied in an amount of 75 to 1,500 kg / ha directly.