EP1150934A1 - Bioorganic fertilizer - Google Patents

Bioorganic fertilizer

Info

Publication number
EP1150934A1
EP1150934A1 EP99973541A EP99973541A EP1150934A1 EP 1150934 A1 EP1150934 A1 EP 1150934A1 EP 99973541 A EP99973541 A EP 99973541A EP 99973541 A EP99973541 A EP 99973541A EP 1150934 A1 EP1150934 A1 EP 1150934A1
Authority
EP
European Patent Office
Prior art keywords
microorganisms
species
bioorganic fertilizer
fertilizer
oil
Prior art date
Legal status (The legal status 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 status listed.)
Withdrawn
Application number
EP99973541A
Other languages
German (de)
French (fr)
Inventor
Alexandr Jurievich Vinarov
Alexei Jurievich Sementsov
Tatiyana Vasilievna Ipatova
Viktor Ivanovich Soloviev
Tatiyana Efimovna Sidorenko
Sergei Vladimirovich Tishkin
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Soil Biogenics Ltd
Original Assignee
" Piksa Inter" Ltd
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 " Piksa Inter" Ltd filed Critical " Piksa Inter" Ltd
Publication of EP1150934A1 publication Critical patent/EP1150934A1/en
Withdrawn legal-status Critical Current

Links

Classifications

    • C—CHEMISTRY; METALLURGY
    • C05—FERTILISERS; MANUFACTURE THEREOF
    • C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F3/00—Fertilisers from human or animal excrements, e.g. manure
    • C—CHEMISTRY; METALLURGY
    • C05—FERTILISERS; MANUFACTURE THEREOF
    • C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F11/00—Other organic fertilisers
    • C05F11/08—Organic fertilisers containing added bacterial cultures, mycelia or the like
    • C—CHEMISTRY; METALLURGY
    • C05—FERTILISERS; MANUFACTURE THEREOF
    • C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • C05F17/80—Separation, elimination or disposal of harmful substances during the treatment
    • Y—GENERAL 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
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • Y—GENERAL 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
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00—Technologies for the production of fuel of non-fossil origin
    • Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
    • Y—GENERAL 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
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00—Technologies relating to chemical industry
    • Y02P20/141—Feedstock
    • Y02P20/145—Feedstock the feedstock being materials of biological origin
    • Y—GENERAL 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
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00—Technologies for solid waste management
    • Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Definitions

  • the present invention relates to the field of biotechnology, namely, to agricultural waste processing, in particular, to the processing of manure and poultry dung, and can be used for the rehabilitation of oil- and oil product-polluted soils, fertilizing of humus-depleted soils, and crop increasing.
  • Manure especially rotten, i.e., bacteria-affected one, has been the basic agricultural fertilizer since the ancient times.
  • rotten i.e., bacteria-affected one
  • bioorganic fertilizer according to EP 0445102 C 05 F 3/00 Application of 1991, which is a preliminarily fermented mixture of liquid and solid animal excrements and organic materials, mixed with greenery and composted.
  • a drawback of this bioorganic fertilizer is its low efficiency for the rehabilitation of oil- and oil product-polluted soils and complex preparation procedure.
  • the closest counterpart of the present invention is the bioorganic fertilizer according to
  • the technical problem solved by the present invention is the development of an ecologically safe bioorganic fertilizer convenient for oil- and oil product-polluted soil rehabilitation and amelioration of humus-depleted soils.
  • the practical result of the present invention is a considerable improvement of the ecological situation due to soil purification from oil and oil products with further involvement of the purified soils into the agricultural turnover.
  • the said result is achieved by exposing manure and poultry dung to microbiological fermentation and adding an active nonpathogenic oil-destructing strain or strain association in an amount of less than 0.2 wt.%.
  • This microorganism strains or association are yeast and/or bacterial non-pathogenic culture of Endomycopsis fibuligera, Pseudomonas species, Corynebacterium species, Pseudomonas pseudoalkaligenes, Methanobacterium species, or the like.
  • the oil-destructing strains can be introduced into the fertilizer during or after microbiological . fermentation.
  • the bioorganic fertilizer may contain nitrogen, potassium, phosphorus, and micro- or macroelement sources in amounts necessary for vegetation.
  • Microbiological fermentation can be applied to fresh or rotten manure, which can be mixed with other organic wastes before the processing.
  • Microbiological fermentation is performed in a conventional manner by introducing a fertile substance containing nitrogen, potassium, phosphorus, and micro- or macroelement sources necessary for the vital activity of manure processing microorganisms. If necessary, additional amounts of nitrogen, potassium, phosphorus, and micro- or macroelement sources can be mixed with the fertilized manure at this stage in order to auspice the development of oil- processing microorganisms in the rehabilitated soil.
  • the bioorganic fertilizer may contain aerobic and/or anaerobic microorganisms, and the contents of macro- and microelements and nutrients are determined by the soil condition.
  • manure and poultry dung are loaded into a fermenter of any design together with a necessary amount of nutrients and, if necessary, water.
  • a manure fermenting microorganism culture is added, appropriate process conditions are produced, and the manure fermentation process is initiated. If the fermentation is performed at oil- or oil product-polluted sites, then the manure to be processed is compounded with oil and oil product biodegrading microorganisms in an amount of 0.2 wt.% and, if necessary, appropriate fertilizing elements, such as potassium and ammonia salts of phosphorus acids or complete ammonium phosphate fertilizers in amounts required for microorganism strain development and soil rehabilitation.
  • appropriate fertilizing elements such as potassium and ammonia salts of phosphorus acids or complete ammonium phosphate fertilizers in amounts required for microorganism strain development and soil rehabilitation.
  • bioorganic fertilizer is introduced into the polluted soil using conventional methods. If the fermentation is performed at cattle or poultry farms, the fermented manure or dung is transported to the soil rehabilitation site, where it is additionally blended with mineral substances, growth activators, and a culture of oil and oil product biodegrading bacteria in the same amounts, and then spread in the polluted soil using a conventional method.
  • Liquid native poultry dung is loaded into a circulation-agitated airlifting fermenter
  • microelements i.e. copper, iron, zinc, and molybdenum salts in a total amount of 0.1% of the
  • microorganism growth activator i.e. an ammonia salt of
  • arylacetic acid in a concentration of 10 "5 wt.%. After that the mixture is fermented for 70 hours. The thus prepared bioorganic fertilizer is then spread uniformly over an oil product- polluted soil area, and the soil is plowed in.
  • the claimed bioorganic fertilizer has allowed 72% of the test oil-polluted soil area formerly inapplicable for cultivation to be involved into the agricultural turnover.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Biochemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Toxicology (AREA)
  • Engineering & Computer Science (AREA)
  • Biotechnology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Microbiology (AREA)
  • Molecular Biology (AREA)
  • Fertilizers (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The fertilizer contains manure and poultry dung processed by microbiological fermentation and oil and oil product degrading microorganisms or microorganism association. The preferred content of microorganisms or microorganism association is within 0.2 wt.%.

Description

Bioorganic Fertilizer
The present invention relates to the field of biotechnology, namely, to agricultural waste processing, in particular, to the processing of manure and poultry dung, and can be used for the rehabilitation of oil- and oil product-polluted soils, fertilizing of humus-depleted soils, and crop increasing.
Manure, especially rotten, i.e., bacteria-affected one, has been the basic agricultural fertilizer since the ancient times. However, a drawback of natural bacterial manure processing
is the significant process duration caused by the absence of mineral fertilizers and the small volume of initial bacterial cultures involved in manure processing.
A notable number of artificial bioorganic fertilizers have been developed over the recent time.
There is the bioorganic fertilizer according to EP 0445102 C 05 F 3/00 Application of 1991, which is a preliminarily fermented mixture of liquid and solid animal excrements and organic materials, mixed with greenery and composted. A drawback of this bioorganic fertilizer is its low efficiency for the rehabilitation of oil- and oil product-polluted soils and complex preparation procedure.
There is a fertilizer made of composted vegetable waste mixed with cattle rumination
products (SU Inventor's Certificate 1578117 C 05 F 11/00, 1990). A disadvantage of this fertilizer is the low biological nutrition value and the low efficiency for the rehabilitation of oil-
and oil product-polluted soils.
The closest counterpart of the present invention is the bioorganic fertilizer according to
SU Inventor's Certificate 294825 C 05 F 3/00, 1971, i.e. manure processed by methane bacterial cultures. A drawback of this invention is the low efficiency for the rehabilitation of
oil- and oil product-polluted soils. The technical problem solved by the present invention is the development of an ecologically safe bioorganic fertilizer convenient for oil- and oil product-polluted soil rehabilitation and amelioration of humus-depleted soils.
The practical result of the present invention is a considerable improvement of the ecological situation due to soil purification from oil and oil products with further involvement of the purified soils into the agricultural turnover.
The said result is achieved by exposing manure and poultry dung to microbiological fermentation and adding an active nonpathogenic oil-destructing strain or strain association in an amount of less than 0.2 wt.%. This microorganism strains or association are yeast and/or bacterial non-pathogenic culture of Endomycopsis fibuligera, Pseudomonas species, Corynebacterium species, Pseudomonas pseudoalkaligenes, Methanobacterium species, or the like. The oil-destructing strains can be introduced into the fertilizer during or after microbiological . fermentation. The bioorganic fertilizer may contain nitrogen, potassium, phosphorus, and micro- or macroelement sources in amounts necessary for vegetation. Microbiological fermentation can be applied to fresh or rotten manure, which can be mixed with other organic wastes before the processing.
Microbiological fermentation is performed in a conventional manner by introducing a fertile substance containing nitrogen, potassium, phosphorus, and micro- or macroelement sources necessary for the vital activity of manure processing microorganisms. If necessary, additional amounts of nitrogen, potassium, phosphorus, and micro- or macroelement sources can be mixed with the fertilized manure at this stage in order to auspice the development of oil- processing microorganisms in the rehabilitated soil. Depending on the introduction conditions, the bioorganic fertilizer may contain aerobic and/or anaerobic microorganisms, and the contents of macro- and microelements and nutrients are determined by the soil condition. To produce the bioorganic fertilizer, manure and poultry dung are loaded into a fermenter of any design together with a necessary amount of nutrients and, if necessary, water.
After that, a manure fermenting microorganism culture is added, appropriate process conditions are produced, and the manure fermentation process is initiated. If the fermentation is performed at oil- or oil product-polluted sites, then the manure to be processed is compounded with oil and oil product biodegrading microorganisms in an amount of 0.2 wt.% and, if necessary, appropriate fertilizing elements, such as potassium and ammonia salts of phosphorus acids or complete ammonium phosphate fertilizers in amounts required for microorganism strain development and soil rehabilitation. The development of oil pollution biodegrading microorganisms can be accelerated by microorganism growth activators, for
example, by ammonia salts of arylacetic acid in amounts of 10"6 % to 10"4 % by weight. The thus prepared bioorganic fertilizer is introduced into the polluted soil using conventional methods. If the fermentation is performed at cattle or poultry farms, the fermented manure or dung is transported to the soil rehabilitation site, where it is additionally blended with mineral substances, growth activators, and a culture of oil and oil product biodegrading bacteria in the same amounts, and then spread in the polluted soil using a conventional method.
Invention application example.
Liquid native poultry dung is loaded into a circulation-agitated airlifting fermenter,
compounded with potassium phosphate in an amount of 1% of the dung weight,
microelements, i.e. copper, iron, zinc, and molybdenum salts in a total amount of 0.1% of the
dung weight, a suspension of active cultures of Endomycopsis flibuligera Y-2173,
Pseudomonas species B-6782, and Pseudomonas pseudoalkaligenes Y-6783 in a total amount
of 0.15% of the dung weight, and a microorganism growth activator, i.e. an ammonia salt of
arylacetic acid in a concentration of 10"5 wt.%. After that the mixture is fermented for 70 hours. The thus prepared bioorganic fertilizer is then spread uniformly over an oil product- polluted soil area, and the soil is plowed in.
The claimed bioorganic fertilizer has allowed 72% of the test oil-polluted soil area formerly inapplicable for cultivation to be involved into the agricultural turnover.
The introduction of this bioorganic fertilizer has made possible rye cultivating with a mean crop of 4.5% greater than for the reference soil area.
The above examples do not restrict the possible preparation methods and applications of the claimed fertilizer.

Claims

1. A bioorganic fertilizer characterized in that it contains manure or poultry dung exposed to microbiological fermentation, an active nonpathogenic oil and oil product degrading microorganisms or microorganism association in an amount of up to 0.2 wt.%, and a microorganism growth activator in an amount of 10"6% to 10_4%by weight.
2. A bioorganic fertilizer according to Claim 1 , characterized in that it contains additional nutrients and micro- and macroelements necessary for the development of microorganisms or microorganism association and vegetation.
3. A bioorganic fertilizer according to Clam 1 , characterized in that an ammonium salt of arylacetic acid is used as a microorganism growth activator.
4. A bioorganic fertilizer according to Claim 1 , characterized in that yeast and/or bacterial nonpathogenic cultures of Endomycopsis fibuligera, Pseudomonas species, Corynebacterium species, Pseudomonas pseudoalkaligenes, Rhodococcus erythropolis, Erwina species, Alkalingenes species, and Methanobacterium species are used as microorganisms or microorganism associations.
(56) SU 294825 A, 04. 02.71.
RU 2057103 Cl, 27.03.96
Dyadechko V.N. et al., "To Biological Rehabilitation of Oil-Polluted Timber Soils in the
Middle Ob River Area", Pochvovedenis, 1990. AMENDED CLAIMS
[received by the International Bureau on 6 Oanuary 2000 (06.01 .00) ; original claims 1 -4 replaced by new claims 1 -8 (2 pages) ]
1. Bioorganic fertilizer characterized in that it contains manure or poultry dung processed by means of microbiological fermentation, at least one of the active strains of microorganisms from the association of microorganisms or association of microorganisms as a whole, suitable to cause of oil and petroleum products bio-degradation, consisting of nonpathogenic cultures of Endomycopsis fibuligera, Erwina species,
Alcaligenes species in the amount up to 0,2 wt. % , and also ammonium salt of arylacetic acid as a microorganism growth activator in concentration of 1 10"6 - 1 10"4 wt. %.
2. Bioorganic fertilizer, according to Claim 1, characterized in that it additionally contains nutritious substances, including sources of nitrogen, potassium, phosphorus and micro -and macroelements.
3. Bioorganic fertilizer, according to Claim 1 or 2, characterized in that a culture of microorganisms or association of cultures are employed in fertilizer, which are capable to cause bio-degradation of oil and petroleum products wherein, a microorganism growth activator, nutritious substances and micro-and macroelements are introduced during microbiological fermentation processing of manure or poultry dung.
4. Bioorganic fertilizer, according to any of Claims 1 to 3, characterized in that microbiological fermentation applies to fresh or rotten manure or poultry dung.
5. Bioorganic fertilizer, according to Claim 4, characterized in that fresh or rotten manure or poultry dung are mixed with other organic wastes before the processing.
6. Bioorganic fertilizer, according to Claim lor 2, characterized in that a culture of microorganisms or association of cultures which are capable to cause bio-degradation of oil and petroleum products, a microorganism growth activator, nutritious substances are introduced into said processed fertilizer by means of microbiological fermentation of manure or poultry dung.
7. Bioorganic fertilizer, according to any of Claims 1 to 6, characterized in that microbiological fermentation is carried out in an agitated airlifting fermentor. Bioorganic fertilizer according to any of Claims 1 to 7, characterized in that as yeast and/or bacterial microorganisms the following nonpathogenetic cultures are additionly used: cultures of
Pseudomonas species, Corynebacterium species, Pseudomonas pseudoalkaligenes, Rhodococcus erythropolis, Methanobacterium species.
EP99973541A 1998-12-29 1999-05-28 Bioorganic fertilizer Withdrawn EP1150934A1 (en)

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
RU98123358 1998-12-29
RU98123358A RU2141932C1 (en) 1998-12-29 1998-12-29 Bio-organic fertilizer
PCT/RU1999/000179 WO2000039052A1 (en) 1998-12-29 1999-05-28 Bioorganic fertilizer

Publications (1)

Publication Number Publication Date
EP1150934A1 true EP1150934A1 (en) 2001-11-07

Family

ID=20213819

Family Applications (1)

Application Number Title Priority Date Filing Date
EP99973541A Withdrawn EP1150934A1 (en) 1998-12-29 1999-05-28 Bioorganic fertilizer

Country Status (4)

Country Link
EP (1) EP1150934A1 (en)
AU (1) AU4297399A (en)
RU (1) RU2141932C1 (en)
WO (1) WO2000039052A1 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US9249061B2 (en) 2011-11-23 2016-02-02 Cornell University Highly efficient organic fertilizer and components thereof

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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
WO2013109153A1 (en) 2011-12-22 2013-07-25 Chervonyi Volodymyr Microbial organic fertilizers and methods of producing thereof

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GB1277632A (en) * 1970-05-18 1972-06-14 Asahi Kasei Kogyo Kaisha Process for preparing specially activated sludge
US4337077A (en) * 1980-09-09 1982-06-29 Rutherford Joseph P Agricultural inoculant composition
US5610065A (en) * 1991-06-21 1997-03-11 Institute Of Gas Technology Integrated chemical/biological treatment of organic waste
JPH06157176A (en) * 1992-04-10 1994-06-03 Towa Kagaku Kk Microbial fertilizer and production and utilization thereof
KR100291876B1 (en) * 1993-06-04 2001-06-01 오쯔까 유우지로 Carrier and Agricultural Materials
FR2709435B1 (en) * 1993-09-01 1995-09-29 Ceca Sa Method for rehabilitating soil contaminated with hydrocarbons and other biodegradable substances.
RU2093578C1 (en) * 1994-11-18 1997-10-20 Государственный научно-исследовательский институт биосинтеза белковых веществ Method of preparing the food protein product
RU2080383C1 (en) * 1994-12-20 1997-05-27 Государственный научно-исследовательский институт биосинтеза белковых веществ Method of treating oil and gas strata

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See references of WO0039052A1 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US9249061B2 (en) 2011-11-23 2016-02-02 Cornell University Highly efficient organic fertilizer and components thereof

Also Published As

Publication number Publication date
RU2141932C1 (en) 1999-11-27
WO2000039052A1 (en) 2000-07-06
AU4297399A (en) 2000-07-31

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