WO1992003393A1 - Detoxification of soil - Google Patents

Detoxification of soil Download PDF

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Publication number
WO1992003393A1
WO1992003393A1 PCT/US1991/005780 US9105780W WO9203393A1 WO 1992003393 A1 WO1992003393 A1 WO 1992003393A1 US 9105780 W US9105780 W US 9105780W WO 9203393 A1 WO9203393 A1 WO 9203393A1
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WO
WIPO (PCT)
Prior art keywords
soil
micro
organisms
substrate
component
Prior art date
Application number
PCT/US1991/005780
Other languages
French (fr)
Inventor
Thomas T. Yamashita
Original Assignee
Yamashita Thomas T
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Yamashita Thomas T filed Critical Yamashita Thomas T
Priority to EP91915298A priority Critical patent/EP0544759B1/en
Publication of WO1992003393A1 publication Critical patent/WO1992003393A1/en
Priority to GR970401918T priority patent/GR3024323T3/en

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Classifications

    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01CPLANTING; SOWING; FERTILISING
    • A01C1/00Apparatus, or methods of use thereof, for testing or treating seed, roots, or the like, prior to sowing or planting
    • A01C1/06Coating or dressing seed
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G13/00Protecting plants
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G7/00Botany in general
    • A01G7/06Treatment of growing trees or plants, e.g. for preventing decay of wood, for tingeing flowers or wood, for prolonging the life of plants
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01HNEW PLANTS OR NON-TRANSGENIC PROCESSES FOR OBTAINING THEM; PLANT REPRODUCTION BY TISSUE CULTURE TECHNIQUES
    • A01H1/00Processes for modifying genotypes ; Plants characterised by associated natural traits
    • A01H1/02Methods or apparatus for hybridisation; Artificial pollination ; Fertility
    • A01H1/027Apparatus for pollination
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01HNEW PLANTS OR NON-TRANSGENIC PROCESSES FOR OBTAINING THEM; PLANT REPRODUCTION BY TISSUE CULTURE TECHNIQUES
    • A01H4/00Plant reproduction by tissue culture techniques ; Tissue culture techniques therefor
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/10Reclamation of contaminated soil microbiologically, biologically or by using enzymes
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F11/00Other organic fertilisers
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F11/00Other organic fertilisers
    • C05F11/08Organic fertilisers containing added bacterial cultures, mycelia or the like
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G1/00Mixtures of fertilisers belonging individually to different subclasses of C05
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G5/00Fertilisers characterised by their form
    • C05G5/20Liquid fertilisers
    • C05G5/23Solutions
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G5/00Fertilisers characterised by their form
    • C05G5/20Liquid fertilisers
    • C05G5/27Dispersions, e.g. suspensions or emulsions
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10TECHNICAL SUBJECTS COVERED BY FORMER USPC
    • Y10STECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y10S47/00Plant husbandry
    • Y10S47/10Physical and chemical treatment of agricultural soils

Definitions

  • This invention relates to the treatment of soil to improve its characteristics for growing vegetation and it relates more particularly to the treatment of soil that has been contaminated by chemicals such as herbicides and other pesticides.
  • This invention is particularly concerned with the detoxification of soil that has become contaminated by chemicals that have been applied directly to the soil, for example as a herbicide, or indirectly as by drainage of water or moisture from plants that have been treated with a chemical; also indirectly by the decay of plants that have been treated by chemicals and the mixing of the products of decay with the soil.
  • This invention is also concerned with the treatment of contaminated soil generally including the treatment of landfills and other soil which has become contaminated with toxic chemicals of various types which are organic in nature and it may have application to treatment of soil contaminated by metals.
  • soil contaminated with a chemical is treated with a nutrient material which will cause proliferation of micro-organisms that degrade the chemical into non-toxic products.
  • the contaminating chemical has had its intended effect, for example as a herbicide, to rid the soil of residues of the chemical; or the nutrient material may be applied to the soil before application of the toxic chemical to the soil, or at the time of application, or shortly after application of the chemical to the soil.
  • the nutrient material is applied at an early stage, that is before the chemical has had its intended effect, care should be taken to avoid or to minimize interference of the nutrient material with the intended action of the chemical.
  • the effect of the nutrient material through the medium of the micro- organisms proliferated by its presence, may act upon and further degrade an intermediate degradation product of the added chemical.
  • the nutrientmaterial may be addedwith orwithout added micro-organisms. That is, the nutrient material may be added alone to proliferate microbiota already in the soil, or micro-organisms may be added to, or along with the nutrient material.
  • the nutrient material may be any plant nutrient capable of causing proliferation of the desired micro ⁇ organisms but it is preferably a balanced material such as that described in the examples below which include as the major component (other than water) a carbon skeleton/energy component, a macronutrient component including a source of nitrogen and a micro-nutrient component and preferably also a complexing agent such as an alginate, a lignosulfonate, etc.
  • the nutrient material also contains a vitamin/cofactor component.
  • the nutrient material may be applied in various ways, for example by adding it to irrigation water or by sprinkling or spraying it onto the soil or as a dust or granular material which is mixed with the soil, also in the form of a suspension in water.
  • micro-organisms normally present in soil are effective in degrading toxic substances in the soil.
  • these micro-organisms have not been used
  • SUBSTITUTE SHEET efficiently heretofore. For example what may be described as xenobiotic components, that is chemicals that are foreign to the natural soil environment, are seldom degraded by a single species or group of microbes.
  • the natural microbiota in soil are stimulated and nourished to cause the proliferation of many species, some of which will effectively degrade chemicals or will acquire, by natural adaptation, the ability to do so.
  • a balanced nutritive is added to the soil which will favor the rapid proliferation of different species and strains of microbiota.
  • Such balanced nutritive is described in the aforesaid co-pending applications as follows:
  • a buffer is also used to adjust the pH of the composition.
  • Example l illustrates a composition, which is useful in the practice of the invention.
  • Pantothenic acid 0.02 Pantothenic acid
  • the most important macronutrients are nitrogen, phosphorus, potassium and calcium but it is preferred that the others also be present.
  • the more important micronutrients are zinc, iron and manganese but it is preferred that the others also be present.
  • TSI total invert sugar
  • the parent molasses may contain potassium concentrations as much as 2.0-7.0%, it may be necessary to omit potassium nitrate. If potassium nitrate is omitted, the nitrogen may be supplied in total by urea (1.25%). Additionally, inositol levels in molasses may reach levels of 5,800-8,000 ppm, in which case this cofactor may be omitted as well. It is important that the pH of the solution be maintained between 5.0-7.5. This latter requirement maybe addressed by analyzingthe dilutionwater sources and adjusting extreme deviations with buffers. Approximately one quart of phosphate buffer per hundred gallons of diluted mix should meet these needs. If the parent molasses has a pH above 7, the standard addition of citric acid and phosphoric acid will adjust this to a manageable level (most molasses have a pH range of between 5-8) .
  • Keaty J is the trademark of JKT Corporation for a mixture of polyhydroxy organic acids used as a complexing (chelating) agent. Commenting on the enhancement agents, the seaweed extract supplies plant hormoneswhich contributeto regulation ofplantmetabolism; the citric acid and Katy J serve as complexing or chelating agents and assist in the transport/ingestion of other ingredients of the composition; and the xanthan gum functions as a thickening agent to solubilize ingredients that would otherwise precipitate or drop out.
  • the phosphate buffer was potassium phosphate.
  • calcium nitrate (Ca(N0 3 ) 2 - 4 H 2 0) may be used as it is less expensive. Also it contributes to the nitrogen component, therefore the amount of potassium nitrate will be adjusted.
  • Table 1 below lists alternative concentrations of the ingredients.
  • a particular ingredient normally added as such, may be present in another ingredient, e.g. in the water used to dilute the molasses or in one of the other ingredients.
  • ingredients may contain one or more other ingredients.
  • molasses will be included in certain ingredients.
  • SUBSTITUTE SHEET often contain some one or more of nitrogen, phosphorus, potassium and calcium, also vitamins and cofactors. Not all of such ingredients are always in the proper form. For example, some or all of the nitrogen may be in the form of proteins and some of the calcium may be in insoluble form.
  • Nicotinic Acid 0.001- 5.00% Pyridoxine 0.001- 5.00%
  • Microbialstat e.g. Proprionic Acid 0.005- 0.50%
  • composition is to be sprayed, it is preferred to remove solids that will not pass through a 60 mesh screen by passing the CSE component successively through 20, 40 and 60 mesh screens and treating the concentrate or stock solution similarly for the same purpose.
  • the pH may range is preferably 2.0 to 3.5.
  • the stock solution (and the diluted solution ready for application) if it is stored for a substantial length of time) is preferably stored at 65 to 85°F.
  • Dilution for end use may be to 2.5 to 12.5 percent of CSE but preferably the dilution is to 4.0 to 10.0% of CSE, percentages being by weight based on the solution.
  • P-superphosphate single, double and/or triple
  • phosphoric acid ammonium phosphate, ammonium phosphate sulfate, ammonium phosphate nitrate, diammonium phosphate, ammoniated single superphosphate, ammoniated single superphosphate, ammoniated triple superphosphate, nitric phosphates.
  • Mo-molybdic acid calcium molybdate, potassium molybdate, sodium molybdate
  • Co-cobaltic acetate cobaltous acetate, cobaltous chloride, cobaltous oxalate, cobaltous potassium sulfate, cobaltous sulfate
  • B-linoleoyl-a-palmitoyl DL-a-PTCh di-O-hexadecyl (dioleoyl, dipalmitoyl, B-O-methyl-g-O-hexadecyl, B-oleoyl-g-O-hexadecyl, B-palmitoyl-g-O-hexadecyl) , D-a-PTCh dipalmitoyl, L-a-PTCh, B-O- methyl-g-O-octadecyl, L-a-PTCh,
  • Citric acid Ca, K, Na and ammonium lignosulfonates, fulvic acid, ulmic acid, humic acid, Katy-J, EDTA, EDDA, EDDHA, HEDTA, CDTA, PTPA, NTA.
  • Xanthan gum-guar gum gum agar, gum accroides, gum arabic, gum carrageenan, gum damar, gum elemi, gum ghatti, gum guiiac, gum karya, locust bean gum, gum mastic, gum pontianak, gum rosin, gum storax, gum tragacanth Microbialstats
  • Proprionic acid benzoic acid, sorbic acid.
  • CSE Components sugar-mannose, lactose, dextrose, arythrose, fructose, fucose, galactose, glucose, gulose, maltose, polysaccharide, raffinose, ribose, ribulose, rutinose, saccharose, stachyose, trehalose, xylose, xylulose, adonose, amylose, arabinose, fructose phosphate, fucose-p, galactose-p, glucose-p, lactose-p, maltose-p, mannose-p, ribose-p, ribulose-p, xylose-p, xylulose-p, deoxyribose, corn steep liquor, whey, corn sugar, corn syrup, maple syrup, grape sugar, grape syrup, beet sugar, sorghum molasses, cane molasses, calcium lignos
  • Buffers phosphate buffer-acetate buffer, AMP buffer, calcium tartrate, glycine buffer, phosphate citrate buffer, tris buffer.
  • micronutrients listed above the most important are Zn, Fe and Mn, but this component preferably also includes the others in the list.
  • the compositior of Examples 2 and 3 may be used.
  • Example 1 As in Example 1 composition
  • Zinc sulfate 0. 05% w/v zinc sulfate
  • the alga species, Gloeocapsa is cultured in one- half strengthHoagland's Solution supplementedwithonegram per 100 gallons mix of Katy-J.
  • the culture suspension is aerated andprovidedwithconstant lighting (via submersible incandescent lamps with an output of light equivalent to approximately 2.0 Einsteins of light energy per squaremeter per hour) .
  • Approximate duration of incubation is 5-7 days. All culturing is conducted under aseptic conditions.
  • Ps. fluorescens are cultured in fermentation tanks similar to that for Gloeocapsa but without lighting and with a different substrate. Nutrient broth (8 gr/L) is supplemented with Bright Sun (0.4% v/v) . Pseudomonas fluorescens is a fast grower and is generally mature within 48 hours culturing time. The remaining three species require a minimum culturing period of 72 hours and in many cases 120 hours. All operations are conducted aseptically, under constant, low aeration and at 25 degrees C.
  • Morning Sun 1 for soil treatment is recommended for soils which are one or more of the following: (1) alkaline, (2) high in salts, (3) high in clay; also soils which have one or more of the following properties: (4) slow infiltration rates, (5) are low in organic matter, (6) an infertile due to minerals being tied up and unavailable fo_. assimilation, (7) are infested with disease inocula.
  • Alkaline soils are benefitted by microbial activity stimulated by Morning Sun, such activity acting to reduce pH and also to generate a mucilage which is a good soil conditioner.
  • Soils high in salts benefit from the increase in infiltration rate caused by Morning Sun.
  • clay With regard to clay, the texture of clay is altered by such microbial activity, becoming more granular. This in turn leads to enhanced infiltration rates. Due to such microbial activity, organic matter is also increased which benefits the soil.
  • the complexing agent especially lignosulfonate, solubilizes minerals and makes them available to plants.
  • Morning Sun stimulates the growth of antagonists.
  • Random samples of soil from the treated plots were examined by standard technigue to determine microbial counts.
  • the calcium lignosulfonate was a product of Georgia-Pacific Corporation known as LIGNOSITE 50 which is described in literature of that company as a 50% aqueous solution of high purity derived from soft wood and as having the following specification.
  • the water is placed in a mixing vessel equipped with a stirrer. While stirring the calcium lignosulfonate, urea, iron sulfate, manganese sulfate, zinc sulfate, potassium nitrate and vitamin B complex are added in that order and stirring is continued until the ingredients are dissolved in the water. Then the molasses is added followed by the phosphoric acid and stirring is continued until they are dissolved. Phosphoric acid is added as needed to bring the pH to 2.5.
  • Oryzalin (3,5-dinitro-N 4 , N 4 dipropylsulfanilide) 40.4% active ingredient.
  • the composition of Table 1 was injected into micro-sprinkler lines at the rate of 20 gallons of such composition per acre in April.
  • the orchard was irrigated as usual based on a demand of 4 - 5 acre feet per season.
  • Weed growth was determined at the end of four weeks from treatment date and was used as a criterion and/or indicator of herbicide degradation.
  • Microbial colony counts were taken at the end of two weeks from the date of treatment. Standard procedures were used with serial dilution to 10 ⁇ 5 , plating 1 ml aliquots atop nutrient agar. Plates were sealed in parafilm (following air drying for eight hours) and incubated in the dark for 72 hours at 25°C.
  • Numbers represent total number of weeds in each 50 foot of strip per replicated block.
  • the composition of Table 2 was shanked in at 30 gallons/acre with spades on each side of the seedling (approximately 8" on either side) at a depth of 3". Seedlings were irrigated via sprinklers to distribute the material into the root zone.
  • Numbers represent length of longest vine per randomly selected plant.
  • Treflan a product of Elanco Chemical Company, is Trifluralin ( , , -trifluro-2,6-dinitro-N,N-dipropyl-p- toluidine) 44.5% active ingredient applied at 2 pints/acre.
  • SUBSTITUT herbicide Potato vines were stunted, thin-leaved and chlorotic.
  • the composition of Table 2 was applied at the rate of 150 gallons/acre by water through a stationary pivot which delivered a 1/8 mile strip of approximately 15' in width.
  • Ten randomly spaced soil cone samples were taken from the area prior to treatment and sent to a laboratory for gas chro atograph analysis of Assert and Sencor. Sampling was continued at two week intervals. Additional parameters examined included:
  • Assert is a product of American Cyanamid containing
  • active ingredients which are (1) m-toluic acid, 6-(4- isopropyl-4-methyl-5-oxo-2 imidazolin-2-yl) ethyl ester and (2) p-toluic acid, 2-(4-isopropyl-4-methyl-5-oxo-2 imidazolin-2-yl) methyl ester.
  • Sencor is a product of Mobay Chemicals containing 41% active ingredient which is 4-amino-6-(l,l dimethyl- ethyl)-3-(methylthio)-1,2,4-triazine-5(4H)-one.
  • Thevulnerability or resistance of toxic chemicals to attack and degradation by micro-organisms is influenced by several factors including the following:
  • Presence of microbialstatic toxins in the soil which may be the toxic chemical of interest or it may be another substance.
  • the preferred composition of Table 2 is simpler than the composition of Example 1 which is a preferred composition for use as a foliar spray.
  • the Example 1 composition may be used for purposes of the present invention but certain of the minerals are naturally present in soil, hence need not be included in the composition of Table 2 intended for soil treatment. For example magnasium, boron, cobalt, molybdenum and copper are omitted because they are normally present in soil.
  • magnasium, boron, cobalt, molybdenum and copper are omitted because they are normally present in soil.
  • molasses is added first whereas in the mixing procedure for Table 2 it is added next to last. I have found that the presence (as is normal) of dissolved solids in molasses in relatively high proportion inhibits dissolving of other minerals.
  • Calcium lignosulfonate is advantageous in the present invention because it is not colonized, therefore is not consumed as rapidly by micro ⁇ organisms as is molasses and other sugar sources.
  • the approximately equal proportions of calcium lignosulfonate and molasses in the composition of Table 2 provide a longer lasting substrate for micro-organisms; i.e. after most or all of the molasses has been consumed there is still calcium lignosulfonate to provide a substrate.
  • the initial breakdownproducts of calcium lignosulfonate arehumic acids which are good substrates and good complexing agents.
  • This component is to supply carbon skeleton for synthesis of proteins and other molecules and to supply energy for metabolism.
  • Water soluble carbo- hydrates such as sucrose, fructose, glucose and other di- and mono-saccharides are suitable, most commonly in the form of molasses or other byproducts of food manufacture.
  • Commercially available lignosulfonates discussed below under the heading "Complexing Agents,” are also suitable as a CSE source inasmuch as they commonly contain sugars.
  • lignosulfonate is not preferred to use as a complete substitute for molasses, soluble starch or other carbo ⁇ hydrate in a foliar spray because it has a toxic effect when employed in large amount but for purposes of soil treatment it may be used as a complete substitute for molasses or other soluble carbohydrate and is preferably used in relatively large proportions, e.g. 1/2 molasses and 1/2 lignosulfonate.
  • the macronutrients are essential to nutrition and growth. Where some of them are present in adequate quantity in the soil, they may be omitted.
  • the most important macronutrients are N, P and K.
  • micronutrients Zn, Fe and Mn. The others may be omitted but their presence is preferred unless they are present in the soil.
  • folic acid biotin, pantothenic acid, nicotinic acid, riboflavin and thiamine. Others may be omitted but their presence is preferred.
  • this component aside from its use as a CSE agent, is to solubilize other components of the composition which otherwise may precipitate and become non- assimilable or difficultly assimilable and' to mobilize minerals in the soil which might otherwise be unavailable to micro-organisms.
  • a complexing agent such as citric acid, humic acids, lignosulfonate, etc. serves to tie up ions such as iron and other ions and prevent them from forming precipitates. In some cases, e.g. with .DTA, this complexing is by way of a process of chelation. The macronutrient or micronutrient so complexed nevertheless remains assimilable.

Abstract

Compositions for and method of degrading organic chemicals in soil. The composition is a nutrient medium serving as a substrate for microorganisms in the soil, preferably containing a major proportion of a source of carbon skeleton and energy, a macronutrient component preferably including nitrogen and other macronutrients, and a micronutrient component, preferably also a complexing agent and a vitamin/co-factor component. This nutrient material is added to soil, e.g. soil contaminated by a pesticide, to cause proliferation of microorganisms which are effective, or which develop effectiveness to degrade the organic chemicals. Preferably the microorganisms are those naturally present in the soil but useful microorganisms may be added with the nutrient medium.

Description

DETOXIFICATION OF SOIL
This application is a continuation-in-part of the following patent applications: Serial No. 242,951, filed September 9, 1988, entitled "COMPOSITION FOR AND METHOD OF TREATING PLANTS", now abandoned; Serial No. 354,155, filed May 19, 1989, entitled "METHOD OF APPLYING ENERGY, CARBON SKELETON AND NUTRIENT MATERIALS TO VEGETATION"; and Serial No. 490,351, filed March 8, 1990, entitled "METHOD AND COMPOSITION FOR PROMOTINGAND CONTROLLING GROWTH OF PLANTS."
FIELD OF THE INVENTION
This invention relates to the treatment of soil to improve its characteristics for growing vegetation and it relates more particularly to the treatment of soil that has been contaminated by chemicals such as herbicides and other pesticides.
BACKGROUND OF THE INVENTION
In my co-pending applications referred to above, the treatment of soil to improve its properties is described including buffering plant roots from harmful, toxic levels of chemicals and/or elements and degrading of harmful chemicals in soil. This invention is particularly concerned with the detoxification of soil that has become contaminated by chemicals that have been applied directly to the soil, for example as a herbicide, or indirectly as by drainage of water or moisture from plants that have been treated with a chemical; also indirectly by the decay of plants that have been treated by chemicals and the mixing of the products of decay with the soil.
This invention is also concerned with the treatment of contaminated soil generally including the treatment of landfills and other soil which has become contaminated with toxic chemicals of various types which are organic in nature and it may have application to treatment of soil contaminated by metals.
The contamination of soil by chemicals applied to the soil directly or indirectly is a serious problem owing to the persistence of such chemicals in the soil which render it unfit for the raising of crops or of lesser use, and also the growth of other vegetation.
Heretofore soil contaminated by toxic chemicals has been detoxified, at least to some extent, by pH effects and hydrolysis, by photochemical effects and by chemical reactions. Residual pesticides have been degraded by unassisted microbiota, either added as such or naturally present in soil.
Such methods have been undependable and have not had consistent success.
SUBSTITUTE SHEET OBJECTS OF THE INVENTION
It is an object of the invention to provide improvements in the detoxification of contaminated soil.
It is a particular object of the invention to provide a method, and a composition for practice of the method, which are superior to methods and compositions used heretofore and which have one or more of the advantages of economy, speed of results, and a wide spectrum of applications to toxicants.
The above and other objects will be apparent from the ensuing description and the appended claims.
SUMMARY OF THE INVENTION
In accordance with the present invention soil contaminated with a chemical is treated with a nutrient material which will cause proliferation of micro-organisms that degrade the chemical into non-toxic products.
This may be done after the contaminating chemical has had its intended effect, for example as a herbicide, to rid the soil of residues of the chemical; or the nutrient material may be applied to the soil before application of the toxic chemical to the soil, or at the time of application, or shortly after application of the chemical to the soil. Where the nutrient material is applied at an early stage, that is before the chemical has had its intended effect, care should be taken to avoid or to minimize interference of the nutrient material with the intended action of the chemical. Further, the effect of the nutrient material, through the medium of the micro- organisms proliferated by its presence, may act upon and further degrade an intermediate degradation product of the added chemical.
SUBSTITUTE SHEET The nutrientmaterial may be addedwith orwithout added micro-organisms. That is, the nutrient material may be added alone to proliferate microbiota already in the soil, or micro-organisms may be added to, or along with the nutrient material.
The nutrient material may be any plant nutrient capable of causing proliferation of the desired micro¬ organisms but it is preferably a balanced material such as that described in the examples below which include as the major component (other than water) a carbon skeleton/energy component, a macronutrient component including a source of nitrogen and a micro-nutrient component and preferably also a complexing agent such as an alginate, a lignosulfonate, etc. Preferably the nutrient material also contains a vitamin/cofactor component.
The nutrient material may be applied in various ways, for example by adding it to irrigation water or by sprinkling or spraying it onto the soil or as a dust or granular material which is mixed with the soil, also in the form of a suspension in water.
Although the invention is described primarily with respect to toxic chemicals such as pesticides, it is applicable to the degradation of organic materials generally, for example waste materials generally, examples being automobile tires that have been finely shredded and mixed with soil.
DETAILED DESCRIPTION OF THE INVENTION
It is known that micro-organisms normally present in soil are effective in degrading toxic substances in the soil. However these micro-organisms have not been used
SUBSTITUTE SHEET efficiently heretofore. For example what may be described as xenobiotic components, that is chemicals that are foreign to the natural soil environment, are seldom degraded by a single species or group of microbes.
In accordance with the present invention the natural microbiota in soil are stimulated and nourished to cause the proliferation of many species, some of which will effectively degrade chemicals or will acquire, by natural adaptation, the ability to do so.
For that purpose, and in the preferred practice of the invention, a balanced nutritive is added to the soil which will favor the rapid proliferation of different species and strains of microbiota. Such balanced nutritive is described in the aforesaid co-pending applications as follows:
1. Assimilable carbon skeleton/energy component. 2. Macronutrient component.
3. Micronutrient component.
In the preferred composition the following additional components are also present:
4. Vitamin/cofactor component.
5. Enhancement agent component.
A buffer is also used to adjust the pH of the composition.
Example l below illustrates a composition, which is useful in the practice of the invention.
EXAMPLE 1
SUBSTITUTE SHEET Sugar beet molasses was used as stock material and source of energy and carbon skeleton. The total invert sugar (TSI) level was brought to 40% by dilution with water. Following are ingredients used to make the molasses blend:
Figure imgf000008_0001
Figure imgf000008_0002
Pantothenic acid 0.02 Pantothenic acid
SUBSTITUTE SHEET
Figure imgf000009_0001
Molasses 40% (TSI) Beet molasses
Buffers
Phosphate buffer 0.02% Phosphate buffer (pH=6)
The most important macronutrients are nitrogen, phosphorus, potassium and calcium but it is preferred that the others also be present. The more important micronutrients are zinc, iron and manganese but it is preferred that the others also be present.
The term "Enhancement Agents" used above is intended to include complexing agents, gums and growth regulators. See the discussion below under the caption "Discussion of Components."
Mixing Instructions
While under rapid mechanical or hydraulic agitation, water and two thirds of the total molasses volume are mixed. The amount of added water should represent approximately 15% of the molasses volume. Ingredients are then slowly metered into the batch in the following order:
1. Citric acid 2. Katy-J Complexing Agent
3. Phosphoric acid
4. Nitrogen
5. Potassium
6. Micronutrients (separately) 7. Vitamins and cofactors
8. Seaweed extract
9. Xanthan gum
Water is again added to the mix to establish a total invert sugar (TSI) concentration of κ40%. As the TSI of molasses may vary, necessary water volumes may vary accordingly.
As the parent molasses may contain potassium concentrations as much as 2.0-7.0%, it may be necessary to omit potassium nitrate. If potassium nitrate is omitted, the nitrogen may be supplied in total by urea (1.25%). Additionally, inositol levels in molasses may reach levels of 5,800-8,000 ppm, in which case this cofactor may be omitted as well. It is important that the pH of the solution be maintained between 5.0-7.5. This latter requirement maybe addressed by analyzingthe dilutionwater sources and adjusting extreme deviations with buffers. Approximately one quart of phosphate buffer per hundred gallons of diluted mix should meet these needs. If the parent molasses has a pH above 7, the standard addition of citric acid and phosphoric acid will adjust this to a manageable level (most molasses have a pH range of between 5-8) .
Storing thematerial between temperatures of 60-80 degrees F is advisable to prolong the activity of
SUBSTITUTE SHEET ingredients. Dilutions for actual spray applications should try to achieve a final TSI between 4-10%.
The many crops to be treated may vary in requirements with respect to species, season and an assortment of environmental factors. It would then be necessary to adjust concentrations of the various ingredients. Workable alternative ranges of these concentrations along with alternative sources are presented.
In the above "Katy J" is the trademark of JKT Corporation for a mixture of polyhydroxy organic acids used as a complexing (chelating) agent. Commenting on the enhancement agents, the seaweed extract supplies plant hormoneswhich contributeto regulation ofplantmetabolism; the citric acid and Katy J serve as complexing or chelating agents and assist in the transport/ingestion of other ingredients of the composition; and the xanthan gum functions as a thickening agent to solubilize ingredients that would otherwise precipitate or drop out.
The phosphate buffer was potassium phosphate.
Instead of using calcium gluconate as the source of calcium, calcium nitrate (Ca(N03)2 - 4 H20) may be used as it is less expensive. Also it contributes to the nitrogen component, therefore the amount of potassium nitrate will be adjusted.
Table 1 below lists alternative concentrations of the ingredients. In a given situation a particular ingredient, normally added as such, may be present in another ingredient, e.g. in the water used to dilute the molasses or in one of the other ingredients.
As stated above certain ingredients may contain one or more other ingredients. For example, molasses will
SUBSTITUTE SHEET often contain some one or more of nitrogen, phosphorus, potassium and calcium, also vitamins and cofactors. Not all of such ingredients are always in the proper form. For example, some or all of the nitrogen may be in the form of proteins and some of the calcium may be in insoluble form.
RANGE OF PROPORTIONS
BRIGHT SUN TABLE 1
A. Carbon Skeleton/Energy Component - 25.00 - 70.00%
B. Macronutrient Component - Nitrogen 0.30 - 15.00%
Phosphorus 0.20 - 5.00%
Potassium 0.30 - 5.00%
Calcium 0.10 - 5.00%
Magnesium 0.05 - 1.50% Sulfur 0.10 - 5.00%
C. Micronutrien Component -
Zinc 0.05 - 2.00%
Manganese 0.05 - 2.00% Iron 0.05 - 2.00%
Copper 0.01 - 0.10%
Boron 0.004- 0.05%
Molybdenum 0.001- 0.02%
Cobalt 0.001- 0.02%
D. Complexing Agen (s) -
Citric Acid, etc. ... 0.005- 5.00%
Lignosulfonate 0.005- 5.00-70.00' E. Vitamin-Cofactor Component -
Folic Acid 0.001- 5.00%
Thiamine 0.001- 5.00%
Riboflavin 0.001- 5.00%
Nicotinic Acid 0.001- 5.00% Pyridoxine 0.001- 5.00%
Biotin 0.001- 5.00%
Pantothenic Acid .... 0.001- 5.00%
Cyanocobalamin 0.001- 5.00%
Phosphatidylcholine . 0.001- 5.00% Inositol 0.001- 5.00%
PABA 0.001- 5.00%
F. Natural Source of Growth Regulator -
Seaweed Extract ...... 0.025- 5.00%
G. Microbialstat, e.g. Proprionic Acid 0.005- 0.50%
SUBSTITUTE SHEET H. Gum, e.g. Xanthan Gum 0.0005- 0.10%
Where the composition is to be sprayed, it is preferred to remove solids that will not pass through a 60 mesh screen by passing the CSE component successively through 20, 40 and 60 mesh screens and treating the concentrate or stock solution similarly for the same purpose. The pH may range is preferably 2.0 to 3.5. The stock solution (and the diluted solution ready for application) if it is stored for a substantial length of time) is preferably stored at 65 to 85°F. Dilution for end use may be to 2.5 to 12.5 percent of CSE but preferably the dilution is to 4.0 to 10.0% of CSE, percentages being by weight based on the solution.
Alternative sources of the ingredients are listed below.
Macronutrients N-ammonium nitrate, monoammoniu phosphate, ammonium phosphate sulfate, ammonium sulfate, ammonium phosphatenitrate, diammonium phosphate, ammoniated single superphosphate, ammoniated triple superphosphate, nitric phosphates, ammonium chloride, aqua ammonia, ammonia-ammonium nitrate solutions, calcium ammonium nitrate, calcium nitrate, calcium cyanamide, sodium nitrate, urea, urea-formaldehyde, urea-ammonium nitrate solution, nitrate of soda potash, potassium nitrate, amino acids, proteins, nucleic acids
P-superphosphate (single, double and/or triple) , phosphoric acid, ammonium phosphate, ammonium phosphate sulfate, ammonium phosphate nitrate, diammonium phosphate, ammoniated single superphosphate, ammoniated single superphosphate, ammoniated triple superphosphate, nitric phosphates.
STITUTE SHEET potassium pyrophosphates, sodium pyrophosphate, nucleic acid phosphates K-potassium chloride, potassium sulfate, potassium gluconate, sulfate of potash magnesia, potassium carbonate, potassium acetate, potassium citrate, potassium hydroxide, potassium manganate, potassium phosphate, potassium molybdate, potassium thiosulfate, potassium zinc sulfate Ca-calcium ammonium nitrate, calcium nitrate, calcium cyanamide, calcium acetate, calcium acetylsalicylate, calcium borate, calcium borogluconate, calcium carbonate, calcium chloride, calcium citrate, calcium ferrous citrate, calcium glycerophosphate, calcium lactate, calcium oxide, calcium pantothenate, calcium proprionate, calcium saccharate, calcium sulfate, calcium tartrate
Mg-magnesium oxide, dolomite, magnesium acetate, magnesium bensoate, magnesium bisulfate, magnesium borate, magnesium chloride, magnesium citrate, magnesium nitrate, magnesium phosphate, magnesium salicylate, magnesium sulfate S-ammonium sulfate, ammonium phosphate sulfate, calcium sulfate, potassium sulfate, magnesium sulfate, sulfuric acid, cobalt sulfate, copper sulfate, ferric sulfate, ferrous sulfate, sulfur, cysteine, methionine
Micronutrients Zn-zinc oxide, zinc acetate, zinc bensoate, zinc chloride, zinc citrate, zinc nitrate, zinc salicylate, ziram Fe-ferric chloride, ferric citrate, ferric fructose, ferric glycerophosphate, ferric nitrate, ferric oxide (saccharated) , ferrous chloride, ferrous citrate ferrous fumarate, ferrous gluconate, ferrous succinate
BSTITUTE SHEET Mn-manganese acetate, manganese chloride, manganese nitrate, manganese phosphate Cu-cupric acetate, cupric butyrate, cupric chlorate, cupric chloride, cupric citrate, cupric gluconate, cupric glycinate, cupric nitrate, cupric salicylate, cuprous acetate, cuprous chloride B-calcium borate, potassium borohydride, borax, boron trioxide, potassium borotartrate, potassium tetraborate, sodium borate, sodium borohydride, sodium tetraborate
Mo-molybdic acid, calcium molybdate, potassium molybdate, sodium molybdate Co-cobaltic acetate, cobaltous acetate, cobaltous chloride, cobaltous oxalate, cobaltous potassium sulfate, cobaltous sulfate
Vitamins and Cofactors
Thiamine-thiamine pyrophosphate, thiamine monophosphate, thiamine disulfide, thiamine mononitrate, thiamine phosphoric acid ester chloride, thiamine phosphoric acid ester phosphate salt, thiamine 1,5 salt, thiamine triphosphoric acid ester, thiamine triphosphoric acid salt, yeast, yeast extract Riboflavin-riboflavin acetyl phosphate, flavin adenine dinucleotide, flavin adenine mononucleotide, riboflavin phosphate, yeast, yeast extract
Nicotinic acid-nicotinic acid adenine dinucleotide, nicotinic acid amide, nicotinic acid benzyl ester, nicotinic acid monoethanolamine salt, yeast, yeast extract, nicotinic acid hydrazide, nicotinic acid hydroxamate, nicotinic acid-N-(hydroxymethyl)amide, nicotinic acid methyl ester, nicotinic acid mononucleotide, nicotinic acid nitrile
Pyridoxine-pyridoxal phosphate, yeast, yeast extract
Folic acid-yeast, yeast extract, folinic acid
TITUTE SHΓTΓ Biotin-biotin sulfoxide, yeast, yeast extract, biotin 4-amidobenzoic acid, biotin amidocaproate N-hydroxysuccinimide ester, biotin 6-amidoquinoline, biotin hydrazide, biotin methyl ester, d-biotin-N-hydroxysuccinimide ester, biotin- maleimide, d-biotin p-nitrophenyl ester, biotin propranolal, 5-(N-biotinyl)-3 aminoallyl)-uridine 5'-triphosphate, biotinylated uridine 5'-triphosphate, N-e-biotinyl-lysine Pantothenic acid-yeast, yeast extract, coenzyme A Cyanocobalamin-yeast, yeast extract Phosphatidylcholine-soybean oil, eggs, bovine heart, bovine brain, bovine liver, L-a-phosphatidylcholine, B-acetyl-g-O-alkyl, D-a-phosphatidylcholine(PTCn) , B-acetyl-g-O-hexadecyl,
DL-a-PTCh,B-acetyl-g-O-hexadecyl, L-a-PTCh, B-acetyl-g-0-(octadec-9-cis-enyl) , L-a-PTCh, B-arachidonoyl, g-stearoyl, L-a-PTCh, diarachidoyl,L-a-PTCh, dibehenoyl (dibutyroyl, dicaproyl, dicapryloyl, didecanoyl, dielaidoyl, 12 diheptadecanoyl, diheptanoyl) , DL-a-PTCh dilauroyl, L-a-PTCh dimyristoyl (dilauroyl, dilinoleoyl, dinonanoyl, dioleoyl, dipentadeconoyl, dipalmitoyl, distearoyl, diundecanoyl, divaleroyl,B-elaidoyl-a-palmitoyl,
B-linoleoyl-a-palmitoyl) DL-a-PTCh di-O-hexadecyl (dioleoyl, dipalmitoyl, B-O-methyl-g-O-hexadecyl, B-oleoyl-g-O-hexadecyl, B-palmitoyl-g-O-hexadecyl) , D-a-PTCh dipalmitoyl, L-a-PTCh, B-O- methyl-g-O-octadecyl, L-a-PTCh,
B-(NBD-aminohexanoyl)-g-palmitoyl, L-a-PTCh, B-oleoyl-g-O-palmitoyl (stearoyl) , L-a-PTCh, B-palmitoyl-g-oleoyl, L-a-PTCh, B-palmitoyl-a-(pyren 1-yl) hexanoyl, L-a-PTCh, B(pyren-l-yl)-decanoyl-g-palmitoyl, L-a-PTCh,
B-(pyren-1-yl)-hexanoyl-g-palmitoyl, L-a-PTCh, B- stearoyl-g-oleoyl
SUBSTITUTE SHEET Inositol-inositol monophosphate, inositol macinate, myo-inositol, epi-inositol, myo-inositol 2,2' anhydro-2-c-hydroxymethyl (2-c-methylene-myoinositol oxide), D-myo-inositol 1,4-bisphosphate, DL-myo-inositol 1,2-cyclic monophosphate, myo-inositol dehydrogenase, myo-inositol hexanicotinate, inositol hexaphosphate, myo-inositol hexasulfate, myo-inositol 2-monophosphate, D-myo-inositol 1-monophosphate, DL-myo-inositol 1-monophosphate, D-myo-inositol triphosphate, scyllo-inositol PABA-m-aminobenzoic acid, O-aminobenzoic acid, p-aminobenzoic acid butyl ester, PABA ethyl ester, 3-ABA ethyl ester
Complexing Agents
Citric acid; Ca, K, Na and ammonium lignosulfonates, fulvic acid, ulmic acid, humic acid, Katy-J, EDTA, EDDA, EDDHA, HEDTA, CDTA, PTPA, NTA.
Growth Regulators
Seaweed extract-kelp extract, kinetin, kinetin riboside, benzyladenine, zeatin riboside, zeatin, extract of corn cockle, isopentenyl adenine, dihydrozeatin, indoleacetic acid, phenylacetic acid, indole ethanol, indoleacetaldehyde, indoleacetonitrile, gibberellins (e.g. GA1, GA2, GA3, GA4, GA7, GA38 etc.)
Gum Components
Xanthan gum-guar gum, gum agar, gum accroides, gum arabic, gum carrageenan, gum damar, gum elemi, gum ghatti, gum guiiac, gum karya, locust bean gum, gum mastic, gum pontianak, gum rosin, gum storax, gum tragacanth Microbialstats
Proprionic acid, benzoic acid, sorbic acid.
CSE Components sugar-mannose, lactose, dextrose, arythrose, fructose, fucose, galactose, glucose, gulose, maltose, polysaccharide, raffinose, ribose, ribulose, rutinose, saccharose, stachyose, trehalose, xylose, xylulose, adonose, amylose, arabinose, fructose phosphate, fucose-p, galactose-p, glucose-p, lactose-p, maltose-p, mannose-p, ribose-p, ribulose-p, xylose-p, xylulose-p, deoxyribose, corn steep liquor, whey, corn sugar, corn syrup, maple syrup, grape sugar, grape syrup, beet sugar, sorghum molasses, cane molasses, calcium lignosulfonate sugar alcohol-adonitol, galactitol, glucitol, maltitol, annitol, mannitol-p, ribitol, sorbitol, sorbitol-p, xylitol organic acids-glucuronic acid, a-ketoglutaric acid, galactonic acid, glucaric acid, gluconic acid, pyruvic acid, polygalacturonic acid, saccharic acid, citric acid, succinic acid, malic acid, oxaloacetic acid, aspartic acid, phosphoglyceric acid, fulvic acid, ulmic acid, humic acid nucleotides and bases-adenosine, adenosine-p, adenosine-p-glucose, uridine, uridine-p, uridine-p-glucose, thymine, thymine-p, cytosine, cytosine-p, guanosine, guanosine-p, guanosine-p-glucose, guanine, guanine-p, NADPH, NADH, FMN, FADH
Buffers phosphate buffer-acetate buffer, AMP buffer, calcium tartrate, glycine buffer, phosphate citrate buffer, tris buffer.
SUBSTITUTE SHEET Of the macronutrients listed above, the most important are N, P, K and Ca but this component preferably also includes magnesium and sulfer.
Of the micronutrients listed above, the most important are Zn, Fe and Mn, but this component preferably also includes the others in the list.
If it is desired to employ such a composition including beneficial micro-organisms, the compositior of Examples 2 and 3 may be used.
EXAMPLE 2 - Soil Amendment
Item Concentration Source
Part I Mix:
Example 1 As in Example 1 composition
Katy-J Complexing Agent 5 gr/gal mix Katy-J (JKT Corp.)
Part II Mix: Gloeocapsa sp. 1 trillion cfu fermentation per gallon mix cultures of
Streptomyces griseus
Gleocladium roseum
Bacillus subtilis
Pseudomonas fluorescens
Cellulase 2,500 units/gal Type VII from
Penicillium funiculosum
Alpha amylase 36,000 units/gal Type XA from
Aspergillus oryzae
Glycerol 2 qt./gal glycerol Buffer 8 oz ./gal phosphatebuffer
Zinc sulfate 0. 05% w/v zinc sulfate
Manganese sulfate 0. 05% W/v manganese sulfate
Iron sulfate 0. 05% w/v Ferrous sulfate
The alga species, Gloeocapsa, is cultured in one- half strengthHoagland's Solution supplementedwithonegram per 100 gallons mix of Katy-J. The culture suspension is aerated andprovidedwithconstant lighting (via submersible incandescent lamps with an output of light equivalent to approximately 2.0 Einsteins of light energy per squaremeter per hour) . Approximate duration of incubation is 5-7 days. All culturing is conducted under aseptic conditions.
Gleocladium roseu . B. subtilis. S.. griseus and
Ps. fluorescens are cultured in fermentation tanks similar to that for Gloeocapsa but without lighting and with a different substrate. Nutrient broth (8 gr/L) is supplemented with Bright Sun (0.4% v/v) . Pseudomonas fluorescens is a fast grower and is generally mature within 48 hours culturing time. The remaining three species require a minimum culturing period of 72 hours and in many cases 120 hours. All operations are conducted aseptically, under constant, low aeration and at 25 degrees C.
When mature, the cultures are aliquanted and blended with glycerol, phosphate buffer and enzymes. They are placed in breathe-cap containers and refrigerated immediately (5 degrees C) . Application involves delivery through the irrigation system or comparable means of approximately one gallon Part I Mix + 1 quart part II Mix per acre (rate may vary with soil condition) . EXAMPLE 3 - Soil Treatment Tests
Use of Morning Sun1 for soil treatment is recommended for soils which are one or more of the following: (1) alkaline, (2) high in salts, (3) high in clay; also soils which have one or more of the following properties: (4) slow infiltration rates, (5) are low in organic matter, (6) an infertile due to minerals being tied up and unavailable fo_. assimilation, (7) are infested with disease inocula.
Alkaline soils are benefitted by microbial activity stimulated by Morning Sun, such activity acting to reduce pH and also to generate a mucilage which is a good soil conditioner.
Soils high in salts benefit from the increase in infiltration rate caused by Morning Sun.
With regard to clay, the texture of clay is altered by such microbial activity, becoming more granular. This in turn leads to enhanced infiltration rates. Due to such microbial activity, organic matter is also increased which benefits the soil.
Where the soil is infertile due to tying up of minerals, the complexing agent, especially lignosulfonate, solubilizes minerals and makes them available to plants.
With regard to disease inocula, Morning Sun stimulates the growth of antagonists.
Experiments were carried out September 2 - November 10, 1989 as follows: Morning Sun was applied at the rate
1"Morning Sun" is the name given to the composition of Example 2. of 0.1 gallon on each of two 400 square foot plots and was applied with about 1100 gallons of water.
Random samples of soil from the treated plots, likewise random samples of soil from adjacent untreated plots, were examined by standard technigue to determine microbial counts.
The soil was also evaluated by standard techniques for soil aggregation and for infiltration rates. Results are summarized as follows:
Microbial Counts
Treated Control 164 11.25
Each figure is the mean of four samples.
Soil Aggregate Tests Treated Control
2 5
These are mean values of four samples each and indicate degree of cloudiness of the air dried soil swirled in water. Less cloudiness indicates more aggregation of the soil.
Infiltration Test
Treated Control 0.45 inch per hour 0.15 inch per hour
These figures indicate greater infiltration/perme¬ ability of the treated soil.
However it is preferred to use a composition as set forth in Table 2 below which does not contain added
TE SHEET micro-organisms and to rely upon micro-organisms naturally present in the soil.
TABLE 2
Figure imgf000023_0001
The calcium lignosulfonate was a product of Georgia-Pacific Corporation known as LIGNOSITE 50 which is described in literature of that company as a 50% aqueous solution of high purity derived from soft wood and as having the following specification. CHEMICAL DESCRIPTION
Total solids, % 50.0
Calcium lignin sulfonate, % 40.0
Methoxyl, % 4.2 Reducing sugars (as glucose), % 3.6
Calcium (soluble), % 2.5
Sodium, % 0.5
Insolubles (CaS04 2H20, % 1.5-2.0 pH of 10% solution 5.5
PHYSICAL PROPERTIES
Specific gravity (liquid, 25°/15° 1.252
Gallon weight, lbs 10.4
Heat of combustion, BTU/lb solids 8100 Viscosity, cp at 25°C 700
These materials are mixed as follows: The water is placed in a mixing vessel equipped with a stirrer. While stirring the calcium lignosulfonate, urea, iron sulfate, manganese sulfate, zinc sulfate, potassium nitrate and vitamin B complex are added in that order and stirring is continued until the ingredients are dissolved in the water. Then the molasses is added followed by the phosphoric acid and stirring is continued until they are dissolved. Phosphoric acid is added as needed to bring the pH to 2.5.
Alternative concentrations are provided in Table 3 below:
Figure imgf000025_0001
The following examples will serve to illustrate the practice and advantages of the invention:
EXAMPLE 4 Pistachio Herbicide Strip
Orchard rows of pistachio trees were stripped with Surflan (3 quarts/acre) and Goal (6 pints/acre) in January and watered in by micro-sprinklers. Following are specifications on each herbicide:
Surflan (Elanco Chemical Company)
Oryzalin (3,5-dinitro-N4, N4 dipropylsulfanilide) 40.4% active ingredient.
Goal (Rohm & Haas Chemical Company)
SHEET Oxyfluorfen2-chloro-l-(3-ethoxy-4-nitrophenoxy) 4-(trifluoromethyl) benzene
19.4% active ingredient.
Each herbicide had curtailed weed growth, the treated strips being completely free of weeds. The composition of Table 1 was injected into micro-sprinkler lines at the rate of 20 gallons of such composition per acre in April. The orchard was irrigated as usual based on a demand of 4 - 5 acre feet per season. Weed growth was determined at the end of four weeks from treatment date and was used as a criterion and/or indicator of herbicide degradation. Microbial colony counts were taken at the end of two weeks from the date of treatment. Standard procedures were used with serial dilution to 10~5, plating 1 ml aliquots atop nutrient agar. Plates were sealed in parafilm (following air drying for eight hours) and incubated in the dark for 72 hours at 25°C.
Results
Replications
Treatment 1 2 3 4 Mean
Control 2 0 3 0 1.2 Treated 163 203 197 257 205.0
Note: Numbers represent total number of weeds in each 50 foot of strip per replicated block.
Weed species detected were pigweed, purslane, shepherd's purse, filavee, barnyard grass.
Microbial Population Increases.
SUBSTITUTE SHEET
Figure imgf000027_0001
Note: Numbers represent microbial colony counts at 72 hours following incubation; dilution = 10~4.
The proliferation of microbes in the plots treated with the Table 1 composition indicate the efficacy of the composition in breaking down the herbicides; likewise the growth of weeds.
EXAMPLE 5 Melon Study Method
A melon field had been treated with Treflan. The melon plants were young seedlings. There was visible damage from Treflan residue, the roots of seedlings typically bent near the soil line and swollen for 3" - 6" down towards the tap root. Secondly, nematode galls from diagnosed populations of Meloidogyne incognita (Root - Knot Nematode) were numerous overaging 16 galls per seedling (number of plants examined = 20) . The composition of Table 2 was shanked in at 30 gallons/acre with spades on each side of the seedling (approximately 8" on either side) at a depth of 3". Seedlings were irrigated via sprinklers to distribute the material into the root zone. One month following treatment plants were examined for top and root growth (shoot length and root girth) , galling and/or stunting and root swelling and bending. Root growth was evaluated on a 0 - 5 scale (5 = excellent) . Results were as follows: 1. Top Growth
Figure imgf000028_0001
Note: Numbers represent length of longest vine per randomly selected plant.
2. Nematode Galling
Replications Treatment 1 2 3 4 Mean Control 25 32 27 41 32 Treated 18 13 15 19 16
Note: Numbers represent galls per root (from nematode damage) .
Figure imgf000028_0002
Note: Numbers represent root evaluation ratings with a 0-5 scale and 5 = excellent status.
Treflan, a product of Elanco Chemical Company, is Trifluralin ( , , -trifluro-2,6-dinitro-N,N-dipropyl-p- toluidine) 44.5% active ingredient applied at 2 pints/acre.
EXAMPLE 6 Potato Study Method A potato field was examined with visible Assert
(American Cyanamid) herbicide toxicity. Additionally, the field had also been treated with Sencor (Mobay Chemicals)
SUBSTITUT herbicide. Potato vines were stunted, thin-leaved and chlorotic. The composition of Table 2 was applied at the rate of 150 gallons/acre by water through a stationary pivot which delivered a 1/8 mile strip of approximately 15' in width. Ten randomly spaced soil cone samples were taken from the area prior to treatment and sent to a laboratory for gas chro atograph analysis of Assert and Sencor. Sampling was continued at two week intervals. Additional parameters examined included:
1. full mineral analysis
2. salts, cation exchange capacity
3. total microbial population counts
4. weed growth 5. soil softness or workability
The results of laboratory tests were not available at the time of filing this application. However, beneficial effects of the composition of Table 2 were quite evident. Thus stubble alongside the treated strip had not decayed indicating that micro-organisms had not proliferated which would have caused decay of the stubble whereas stubble in the treated strip had decayed. This was confirmed by micro¬ organism counts, such being greater in the treated strip. It is believed that laboratory tests will establish the breakdown of herbicides in the treated strip. Also noted was recovery of potato plants in the treated strip whereas there was no such recovery in the untreated soil.
Assert is a product of American Cyanamid containing
27% active ingredients which are (1) m-toluic acid, 6-(4- isopropyl-4-methyl-5-oxo-2 imidazolin-2-yl) ethyl ester and (2) p-toluic acid, 2-(4-isopropyl-4-methyl-5-oxo-2 imidazolin-2-yl) methyl ester. Sencor is a product of Mobay Chemicals containing 41% active ingredient which is 4-amino-6-(l,l dimethyl- ethyl)-3-(methylthio)-1,2,4-triazine-5(4H)-one.
Thevulnerability or resistance of toxic chemicals to attack and degradation by micro-organisms is influenced by several factors including the following:
1. Moisture content and oxygen level in the soil. Lack of moisture and/or oxygen favor resistance to degradation.
2. Presence of microbialstatic toxins in the soil, which may be the toxic chemical of interest or it may be another substance.
3. Temperature. Extremes of temperature, that is to say excessive cold or heat, favor resistance. Alternatively, moderate temperature favors the growth of micro-organisms which are desired.
4. Chemical interactions which immobilize substrates. For example iron or phosphorus may. act to harden soil and make it impervious to the nutrient material.
5. Minimal or no access of microbes to the toxic chemical.
6. Low substrate or nutrient levels.
Commenting on the factors listed above, if there are no temperature extremes and if moisture and oxygen are abundant, i.e. factors 1 and 3 are favorable, if an abundant nutrient (substrate) level is available, factors 2, 4 and 5 can be overcome. Thus favorable factors 1 and 3 combined with favorable factor 6 will cause microbial communities to increase dramatically and this will mitigate unfavorable factors 2, 4 and 5. As the microbial population increases the chemical degrading and detoxifying effects will increase. For example if a .chemical, or a partial degradation product of a chemical, is resistant to a particular species of micro-organism, an increase in the population of that species may overcome the difficulty (a mass effect) or a mutated species may evolve which is effective. The multiplication of many species is favorable because the chance of an effective species (effective to degrade a chemical) being multiplied is enhanced by favorable factors 1, 3 and 6.
Commenting further on the description above of the invention:
The preferred composition of Table 2 is simpler than the composition of Example 1 which is a preferred composition for use as a foliar spray. The Example 1 composition may be used for purposes of the present invention but certain of the minerals are naturally present in soil, hence need not be included in the composition of Table 2 intended for soil treatment. For example magnasium, boron, cobalt, molybdenum and copper are omitted because they are normally present in soil. Also, in the mixing procedure of Example 1 molasses is added first whereas in the mixing procedure for Table 2 it is added next to last. I have found that the presence (as is normal) of dissolved solids in molasses in relatively high proportion inhibits dissolving of other minerals. Calcium lignosulfonate is advantageous in the present invention because it is not colonized, therefore is not consumed as rapidly by micro¬ organisms as is molasses and other sugar sources. The approximately equal proportions of calcium lignosulfonate and molasses in the composition of Table 2 provide a longer lasting substrate for micro-organisms; i.e. after most or all of the molasses has been consumed there is still calcium lignosulfonate to provide a substrate. Further, the initial breakdownproducts of calcium lignosulfonate arehumic acids which are good substrates and good complexing agents.
Discussion of Components (1) The Assimilable Carbon
Skeleton/Energy (CSE) Component
The function of this component is to supply carbon skeleton for synthesis of proteins and other molecules and to supply energy for metabolism. Water soluble carbo- hydrates such as sucrose, fructose, glucose and other di- and mono-saccharides are suitable, most commonly in the form of molasses or other byproducts of food manufacture. Commercially available lignosulfonates, discussed below under the heading "Complexing Agents," are also suitable as a CSE source inasmuch as they commonly contain sugars. It is not preferred to use lignosulfonate as a complete substitute for molasses, soluble starch or other carbo¬ hydrate in a foliar spray because it has a toxic effect when employed in large amount but for purposes of soil treatment it may be used as a complete substitute for molasses or other soluble carbohydrate and is preferably used in relatively large proportions, e.g. 1/2 molasses and 1/2 lignosulfonate.
(2) The Macronutrient Component
The macronutrients are essential to nutrition and growth. Where some of them are present in adequate quantity in the soil, they may be omitted.
The most important macronutrients are N, P and K.
(3) Micronutrient Component
The most important micronutrients are Zn, Fe and Mn. The others may be omitted but their presence is preferred unless they are present in the soil.
SUBSTITUTE SHEET (4) Vitamin/Cofactor Component
The most important are folic acid, biotin, pantothenic acid, nicotinic acid, riboflavin and thiamine. Others may be omitted but their presence is preferred.
(5) Complexing Agents
The function of this component, aside from its use as a CSE agent, is to solubilize other components of the composition which otherwise may precipitate and become non- assimilable or difficultly assimilable and' to mobilize minerals in the soil which might otherwise be unavailable to micro-organisms.
A complexing agent such as citric acid, humic acids, lignosulfonate, etc. serves to tie up ions such as iron and other ions and prevent them from forming precipitates. In some cases, e.g. with .DTA, this complexing is by way of a process of chelation. The macronutrient or micronutrient so complexed nevertheless remains assimilable.
It will therefore be apparent that new and useful compositions for and methods of detoxification of soil have been provided.

Claims

I CLAIM:
1. A method of degrading an organic chemical in soil which comprises incorporating in the soil a nutrient medium favoring proliferation of micro-organisms added to or naturally present in the soil which directly attack and degrade the organic chemical or which acquire the ability to attack and degrade the toxic chemical.
2. The method of Claim 1 wherein the micro¬ organisms are primarily or entirely those present in the soil before incorporating the nutrient medium.
3. The method of Claim 1 in which the nutrient medium comprises a carbon skeleton/energy component, a macronutrient component including nitrogen and a micronutrient component, such components being present in quantities and proportions such that themedium causes rapid proliferation of soil micro-organisms.
4. The method of Claim 3 wherein the nutrient medium includes a complexing agent which assists in the ingestion of the nutrient medium by micro-organisms and to mobilize minerals that are tied up in the soil and to make them available to the micro-organisms.
5. The method of Claim 4 in which the nutrient medium includes a vitamin/co-factor component.
6. The method of Claim 5 in which the nutrient medium includes a lignosulfonate which acts as a complexing agent and also as a carbon skeleton/energy component and is present in a quantity sufficient to contribute substantially to the carbon skeleton/energy requirements of said micro-organisms.
7. A method of degrading toxic chemicals in soil which contains naturally, or to which are added, micro¬ organisms, such micro-organisms being (1) capable of using such toxic chemical or chemicals as a substrate and degrading the same or being (2) capable, when provided with a suitable substrate, of developing micro-organisms having such capability, saidmethod comprisingmixingwith the soil a substrate selected and in a quantity sufficient to cause proliferation of such micro-organisms in quantity sufficient to degrade the chemical or chemicals.
8. The method of Claim 7 wherein said substrate includes all of the carbon skeleton/energy, macronutrient, micronutrient, vitamin/co-factor and complexing components needed for such proliferation, such substrate being used in quantity sufficient to accomplish the intended purpose.
9. A method of biodegradation of organic substances which comprises providing soil mixed with added organic material which it is desired to degrade, providing also as a natural component of the soil or by adding to and mixing with the soil micro-organisms which (1) are capable of acting upon such organic material as a substrate to degrade it or (2) are capable of developing micro-organisms having capability (1) , providing in the soil an added substrate which causes such micro-organisms to proliferate and allowing the micro-organisms to so proliferate and upon exhaustion of the added substrate to act upon such organic substance.
PCT/US1991/005780 1990-08-23 1991-08-21 Detoxification of soil WO1992003393A1 (en)

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Cited By (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2695138A1 (en) * 1992-08-31 1994-03-04 Elf Aquitaine New biodegradation additive.
FR2695139A1 (en) * 1992-08-31 1994-03-04 Elf Aquitaine Biodegradation additive contg. aminoacid as assimilable source of nitrogen
US5525139A (en) * 1993-07-12 1996-06-11 Gill; Paul E. Process for bioremediation of soils
US5609668A (en) * 1994-09-30 1997-03-11 Gill; Paul E. Spill clean-up process
US5646157A (en) * 1991-12-05 1997-07-08 Novartis Corporation Disposal of obsolete treated seed
WO1999045782A1 (en) * 1998-03-12 1999-09-16 Earth Alive Resources Inc. Method for treating soil for the control of soil borne plant pathogens
EP1792877A1 (en) * 2005-12-01 2007-06-06 Tekniska Verken I Linköping AB A method, an additive, and a device for digesting organic matter
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US8739734B2 (en) 2011-12-02 2014-06-03 Paul E. Gill Spill clean up material and pet litter, and methods of making and using same
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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5582627A (en) * 1988-09-09 1996-12-10 Yamashita; Thomas T. Detoxification of soil
US6309440B1 (en) * 1998-08-25 2001-10-30 Thomas T. Yamashita Method and composition for promoting and controlling growth of plants
US5632799A (en) * 1994-09-23 1997-05-27 Tennessee Valley Authority Dried particulate, hydrophilic gel as micronutrient delivery system
EP0985347A4 (en) * 1996-05-07 2002-10-09 Hiroshi Kawai Effervescent preparation for plants
US6020185A (en) * 1997-05-23 2000-02-01 Geovation Consultants, Inc. Method and composition for the anaerobic biodegradation of toxic compounds
US6165245A (en) * 1998-09-09 2000-12-26 Yamashita; Thomas T. Foliar fertilizer and method for using the same
US6187326B1 (en) * 1998-12-29 2001-02-13 Thomas T. Yamashita Soil amendment composition
US6241795B1 (en) 1999-04-16 2001-06-05 Miller Chemical And Fertilizer Corporation Soluble fertilizer formulation
US6383245B1 (en) 2000-04-05 2002-05-07 Thomas T. Yamashita Aqueous mineral compositions and methods for their use
US6871446B1 (en) * 2000-10-23 2005-03-29 Thomas T. Yamashita Microbial blend compositions and methods for their use
US6620611B2 (en) * 2001-01-06 2003-09-16 Geovation Technologies, Inc. Solid-chemical composition for sustained release of organic substrates and complex inorganic phosphates for bioremediation
ITLT20020003A1 (en) * 2002-01-21 2003-07-21 Domenico Terenzio NUTRITIONAL ELEMENTS IN THE FORM OF GLUCONATES, FOR THE PURPOSE OF IMPROVING NUTRITION AND THE DEFENSE OF PLANTS, TO SAFEGUARD THE ENVIRONMENT D
US8486859B2 (en) 2002-05-15 2013-07-16 Bioenergy, Inc. Use of ribose to enhance plant growth
US8741174B1 (en) * 2002-09-20 2014-06-03 Sandia Corporation Reduced weight decontamination formulation for neutralization of chemical and biological warfare agents
US7927616B2 (en) * 2004-01-16 2011-04-19 Thomas T. Yamashita Pesticide compositions and methods for their use
AU2005215846B2 (en) * 2004-02-23 2011-01-27 Caiteng Zhang A solution of metal-polymer chelate(s) and applications thereof
US7906129B2 (en) 2004-03-04 2011-03-15 Thomas T. Yamashita Methods for treating a plant exposed to a phytotoxicant
US20050245398A1 (en) * 2004-04-29 2005-11-03 Healthy Soils, Inc. Biological composition for enhancing vegetation growth
US20090082205A1 (en) * 2004-04-29 2009-03-26 Stock Raymond W Biological composition for generating and feeding microorganisms that are intended for distribution in an agricultural system
US20060196241A1 (en) * 2004-05-20 2006-09-07 Georgia-Pacific Resins, Inc. High nitrogen liquid fertilizer
US20060046936A1 (en) * 2004-08-31 2006-03-02 Travis Teuton Foliar composition for stressed turfgrass and associated method
US20060172888A1 (en) * 2005-02-03 2006-08-03 Roman Blaszczyk Natural grass fertilizer with weed and grub control activity
US7138060B2 (en) * 2005-03-30 2006-11-21 Delta Environmental Consultants, Inc. In situ remediation of contaminated groundwater
US20060288749A1 (en) * 2005-06-22 2006-12-28 Drake Edgar N Iii Inedible egg compositions and methods for organic fertilization of plants
US7513928B2 (en) * 2006-02-21 2009-04-07 Phillips James C High nitrogen liquid fertilizer
US7585826B2 (en) * 2007-03-22 2009-09-08 Well-Being Biochemical Corp. Compositions counteracting pesticides and malodorants
GB2463115B (en) * 2008-09-08 2013-04-10 Schlumberger Holdings Assemblies for the purification of a reservoir or process fluid
US20100261605A1 (en) * 2009-04-08 2010-10-14 Monahan Dennis N Method and apparatus for processing work materials
US9056265B2 (en) 2009-06-05 2015-06-16 Tenfold Technologies, LLC Isolated bioactive compounds and method of use
US8262912B1 (en) * 2009-06-05 2012-09-11 Tenfold Technologies, LLC Isolated bioactive compounds and method of use
GB0913760D0 (en) * 2009-08-06 2009-09-16 Rothamsted Res Ltd A method of reducing nitrate leaching from soil
US8814471B2 (en) * 2009-11-05 2014-08-26 Regenesis Bioremediation Products Method and system for capturing subsurface contaminants
US9365441B2 (en) 2010-12-10 2016-06-14 Robert C Borden Product and method for treatment of soil and groundwater contaminated with pollutants that can be anaerobically bioremediated
US8845232B2 (en) * 2010-12-10 2014-09-30 Robert C. Borden Product and method for treatment of soil contaminated with energetic materials
US9056340B2 (en) 2012-03-30 2015-06-16 Bioremediation Specialists L.L.C. Bioremediation systems, compositions, and methods
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Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4119429A (en) * 1976-03-17 1978-10-10 Judd Ringer Corporation Soil supplement
JPS57158286A (en) * 1981-03-26 1982-09-30 Sumie Hihara Soil improving material having insecticidal effect
JPS61200193A (en) * 1985-03-01 1986-09-04 Katakura Chitsukarin Kk Soil modifier for plant rootsphere
US4952229A (en) * 1983-09-27 1990-08-28 Hugh M. Muir Plant supplement and method for increasing plant productivity and quality

Family Cites Families (30)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2756134A (en) * 1952-08-04 1956-07-24 Ohio Commw Eng Co Soil stabilization
US3353949A (en) * 1964-07-06 1967-11-21 American Cyanamid Co Method for preventing the segregation of mixed fertilizer
JPS4322206Y1 (en) 1965-12-01 1968-09-18
US3640698A (en) * 1970-03-19 1972-02-08 Union Oil Co Fertilizer urea solutions containing micronutrients
US3753722A (en) * 1971-08-27 1973-08-21 Cargill Inc Animal feed supplement
JPS5546999B2 (en) 1971-12-30 1980-11-27
US3846290A (en) * 1972-09-29 1974-11-05 Sun Research Development Reclamation of hydrocarbon contaminated ground waters
US4033745A (en) * 1976-06-03 1977-07-05 Slo Release, Inc. Non-burning storable liquid fertilizer
JPS5362676A (en) 1976-11-18 1978-06-05 Teruhisa Takase Method for producing fertilizers for agricultural crops
US4201564A (en) * 1977-11-15 1980-05-06 Kauzal Gabriel P Organic fertilizer
JPS5755986A (en) * 1980-09-19 1982-04-03 Ooya:Kk Manufacture of soil conditioner
IT1139177B (en) * 1980-09-19 1986-09-24 Elf Aquitaine MICROEMULSION OF NUTRITIONAL SUBSTANCES
US4493895A (en) * 1981-09-24 1985-01-15 Occidental Chemical Corporation Microbial degradation of obnoxious organic wastes into innocuous materials
DE3417133A1 (en) * 1984-05-07 1985-11-07 Schering AG, 1000 Berlin und 4709 Bergkamen LEAF FERTILIZER FOR TARGETED LONG-TERM APPLICATION
US4727031A (en) * 1984-11-08 1988-02-23 International Technology Corporation Nutrient for stimulating aerobic bacteria
US4652294A (en) * 1985-05-31 1987-03-24 Professional Agricultural Management, Inc. Foliar fertilization method and compounds
US4789391A (en) * 1985-07-08 1988-12-06 Reed Lignin Inc. Controlled release formulation for fertilizers
JPS6317814A (en) 1986-07-11 1988-01-25 Karufua Chem Kk Plant growth acceleration and agent therefor
US4849360A (en) * 1986-07-30 1989-07-18 International Technology Corporation Apparatus and method for confining and decontaminating soil
JPH01200193A (en) * 1987-07-21 1989-08-11 Akutoronikusu Kk Temperature stabilizing device for inside of case
US5549729A (en) * 1988-09-09 1996-08-27 Yamashita; Thomas T. Method and composition for promoting and controlling growth of plants
IL91513A (en) * 1988-09-09 1993-07-08 Yamashita Thomas T Method of applying energy, carbon skeleton and nutrient materials to vegetation
US5582627A (en) * 1988-09-09 1996-12-10 Yamashita; Thomas T. Detoxification of soil
US4925802A (en) * 1988-12-21 1990-05-15 Ecova Corporation Method for stimulating biodegradation of halogenated aliphatic hydrocarbons
JPH02279578A (en) 1989-04-18 1990-11-15 Iseki & Co Ltd Fertilizer composing containing coenzyme
US4997469A (en) * 1990-01-10 1991-03-05 Harmony Products, Inc. High integrity, low odor, natural based nitrogenous granules for agriculture
US5387271A (en) * 1990-04-11 1995-02-07 Idaho Research Foundation, Inc. Biological system for degrading nitroaromatics in water and soils
CA2084881C (en) * 1990-06-08 1998-01-06 John Cunningham Controlled-release microbe nutrients and method for bioremediation
US5328497A (en) * 1992-01-21 1994-07-12 Georgia-Pacific Corporation Particulate fertilizer dust control
US5698001A (en) * 1995-10-24 1997-12-16 Rsa Microtech, Incorporated Soil additive

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4119429A (en) * 1976-03-17 1978-10-10 Judd Ringer Corporation Soil supplement
JPS57158286A (en) * 1981-03-26 1982-09-30 Sumie Hihara Soil improving material having insecticidal effect
US4952229A (en) * 1983-09-27 1990-08-28 Hugh M. Muir Plant supplement and method for increasing plant productivity and quality
JPS61200193A (en) * 1985-03-01 1986-09-04 Katakura Chitsukarin Kk Soil modifier for plant rootsphere

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See also references of EP0544759A4 *

Cited By (29)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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WO1994005773A1 (en) * 1992-08-31 1994-03-17 Elf Aquitaine Novel biodegradation additive
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FR2695138A1 (en) * 1992-08-31 1994-03-04 Elf Aquitaine New biodegradation additive.
US5525139A (en) * 1993-07-12 1996-06-11 Gill; Paul E. Process for bioremediation of soils
US5609668A (en) * 1994-09-30 1997-03-11 Gill; Paul E. Spill clean-up process
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US7622286B2 (en) 2005-12-01 2009-11-24 Tekiniska Verken I Linkoping Ab Method, a device and an additive for digesting organic matter
US7947484B2 (en) 2005-12-01 2011-05-24 Tekniska Verken I Linkoping Ab Method, a device, and an additive for digesting organic matter
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PT98749A (en) 1992-07-31
GR3024323T3 (en) 1997-10-31
PT98749B (en) 1999-01-29
PH30895A (en) 1997-12-23
US5582627A (en) 1996-12-10
EP0544759A1 (en) 1993-06-09
AU8424991A (en) 1992-03-17
EP0544759A4 (en) 1994-06-01
US6336772B1 (en) 2002-01-08
EP0544759B1 (en) 1997-07-30
MX174528B (en) 1994-05-23
ES2106786T3 (en) 1997-11-16

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