CN115491331A - A microbial agent that promotes carbon emission reduction in rice straw returning to the field - Google Patents
A microbial agent that promotes carbon emission reduction in rice straw returning to the field Download PDFInfo
- Publication number
- CN115491331A CN115491331A CN202211278840.5A CN202211278840A CN115491331A CN 115491331 A CN115491331 A CN 115491331A CN 202211278840 A CN202211278840 A CN 202211278840A CN 115491331 A CN115491331 A CN 115491331A
- Authority
- CN
- China
- Prior art keywords
- microbial agent
- field
- bacteria
- bacillus
- returning
- 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.)
- Pending
Links
- 239000010902 straw Substances 0.000 title claims abstract description 44
- 235000007164 Oryza sativa Nutrition 0.000 title claims abstract description 30
- 235000009566 rice Nutrition 0.000 title claims abstract description 30
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 title claims abstract description 27
- 229910052799 carbon Inorganic materials 0.000 title claims abstract description 27
- 230000009467 reduction Effects 0.000 title claims abstract description 10
- 240000007594 Oryza sativa Species 0.000 title claims 2
- 230000000813 microbial effect Effects 0.000 title abstract description 40
- 239000003795 chemical substances by application Substances 0.000 title abstract description 31
- 241000894006 Bacteria Species 0.000 claims abstract description 47
- JVTAAEKCZFNVCJ-UHFFFAOYSA-N lactic acid Chemical compound CC(O)C(O)=O JVTAAEKCZFNVCJ-UHFFFAOYSA-N 0.000 claims abstract description 28
- 239000004310 lactic acid Substances 0.000 claims abstract description 14
- 235000014655 lactic acid Nutrition 0.000 claims abstract description 14
- 230000000243 photosynthetic effect Effects 0.000 claims abstract description 13
- 241000193755 Bacillus cereus Species 0.000 claims abstract description 11
- 241000194108 Bacillus licheniformis Species 0.000 claims abstract description 11
- 244000063299 Bacillus subtilis Species 0.000 claims abstract description 11
- 235000014469 Bacillus subtilis Nutrition 0.000 claims abstract description 11
- 240000004808 Saccharomyces cerevisiae Species 0.000 claims description 16
- 241000589220 Acetobacter Species 0.000 claims description 6
- 239000002068 microbial inoculum Substances 0.000 claims 6
- 241000209094 Oryza Species 0.000 abstract description 28
- 239000002689 soil Substances 0.000 abstract description 18
- 230000000694 effects Effects 0.000 abstract description 14
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 abstract description 11
- 241000589212 Acetobacter pasteurianus Species 0.000 abstract description 10
- 239000002131 composite material Substances 0.000 abstract description 10
- 239000003337 fertilizer Substances 0.000 abstract description 7
- 238000000354 decomposition reaction Methods 0.000 abstract description 6
- 238000005516 engineering process Methods 0.000 abstract description 6
- 230000009919 sequestration Effects 0.000 abstract description 6
- 239000001913 cellulose Substances 0.000 abstract description 5
- 229920002678 cellulose Polymers 0.000 abstract description 5
- 235000015097 nutrients Nutrition 0.000 abstract description 5
- 230000009286 beneficial effect Effects 0.000 abstract description 4
- 230000001737 promoting effect Effects 0.000 abstract description 4
- 230000007547 defect Effects 0.000 abstract description 3
- 244000052616 bacterial pathogen Species 0.000 abstract description 2
- 230000004071 biological effect Effects 0.000 abstract description 2
- 230000015556 catabolic process Effects 0.000 abstract description 2
- 238000006731 degradation reaction Methods 0.000 abstract description 2
- 230000007613 environmental effect Effects 0.000 abstract description 2
- 230000000704 physical effect Effects 0.000 abstract description 2
- 241000235342 Saccharomycetes Species 0.000 abstract 2
- 239000002609 medium Substances 0.000 description 14
- 238000000855 fermentation Methods 0.000 description 13
- 230000004151 fermentation Effects 0.000 description 12
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 11
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 8
- 241000193830 Bacillus <bacterium> Species 0.000 description 7
- 150000001875 compounds Chemical class 0.000 description 7
- 239000001888 Peptone Substances 0.000 description 6
- 108010080698 Peptones Proteins 0.000 description 6
- 235000019319 peptone Nutrition 0.000 description 6
- 239000007787 solid Substances 0.000 description 6
- 229920001817 Agar Polymers 0.000 description 5
- WQZGKKKJIJFFOK-GASJEMHNSA-N Glucose Natural products OC[C@H]1OC(O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-GASJEMHNSA-N 0.000 description 5
- 239000008272 agar Substances 0.000 description 5
- 229940041514 candida albicans extract Drugs 0.000 description 5
- 239000008103 glucose Substances 0.000 description 5
- 238000004519 manufacturing process Methods 0.000 description 5
- 239000000203 mixture Substances 0.000 description 5
- 239000012138 yeast extract Substances 0.000 description 5
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 4
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 description 4
- 230000001580 bacterial effect Effects 0.000 description 4
- 235000015278 beef Nutrition 0.000 description 4
- 235000010980 cellulose Nutrition 0.000 description 4
- 238000002360 preparation method Methods 0.000 description 4
- 239000011780 sodium chloride Substances 0.000 description 4
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 description 3
- 229920002472 Starch Polymers 0.000 description 3
- 241000607479 Yersinia pestis Species 0.000 description 3
- 239000012153 distilled water Substances 0.000 description 3
- 239000000284 extract Substances 0.000 description 3
- 230000004720 fertilization Effects 0.000 description 3
- 238000000034 method Methods 0.000 description 3
- 244000005700 microbiome Species 0.000 description 3
- 239000006916 nutrient agar Substances 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- 239000008107 starch Substances 0.000 description 3
- 235000019698 starch Nutrition 0.000 description 3
- 230000002195 synergetic effect Effects 0.000 description 3
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 2
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 2
- 208000035240 Disease Resistance Diseases 0.000 description 2
- 241000233866 Fungi Species 0.000 description 2
- 241000238631 Hexapoda Species 0.000 description 2
- 239000004480 active ingredient Substances 0.000 description 2
- 239000001963 growth medium Substances 0.000 description 2
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 238000003973 irrigation Methods 0.000 description 2
- 230000002262 irrigation Effects 0.000 description 2
- 229920005610 lignin Polymers 0.000 description 2
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 2
- 235000019341 magnesium sulphate Nutrition 0.000 description 2
- 239000002207 metabolite Substances 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 150000007524 organic acids Chemical class 0.000 description 2
- 235000005985 organic acids Nutrition 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 238000009331 sowing Methods 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 235000000346 sugar Nutrition 0.000 description 2
- 208000010444 Acidosis Diseases 0.000 description 1
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 description 1
- 229910000013 Ammonium bicarbonate Inorganic materials 0.000 description 1
- 244000025254 Cannabis sativa Species 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 108090000790 Enzymes Proteins 0.000 description 1
- 102000004190 Enzymes Human genes 0.000 description 1
- 244000068988 Glycine max Species 0.000 description 1
- 235000010469 Glycine max Nutrition 0.000 description 1
- 229920002488 Hemicellulose Polymers 0.000 description 1
- 239000007836 KH2PO4 Substances 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 1
- CKUAXEQHGKSLHN-UHFFFAOYSA-N [C].[N] Chemical compound [C].[N] CKUAXEQHGKSLHN-UHFFFAOYSA-N 0.000 description 1
- 230000036579 abiotic stress Effects 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 230000007950 acidosis Effects 0.000 description 1
- 208000026545 acidosis disease Diseases 0.000 description 1
- 230000003213 activating effect Effects 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- 235000012538 ammonium bicarbonate Nutrition 0.000 description 1
- 239000001099 ammonium carbonate Substances 0.000 description 1
- 230000000844 anti-bacterial effect Effects 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 229910000019 calcium carbonate Inorganic materials 0.000 description 1
- 239000004202 carbamide Substances 0.000 description 1
- 239000005018 casein Substances 0.000 description 1
- BECPQYXYKAMYBN-UHFFFAOYSA-N casein, tech. Chemical compound NCCCCC(C(O)=O)N=C(O)C(CC(O)=O)N=C(O)C(CCC(O)=N)N=C(O)C(CC(C)C)N=C(O)C(CCC(O)=O)N=C(O)C(CC(O)=O)N=C(O)C(CCC(O)=O)N=C(O)C(C(C)O)N=C(O)C(CCC(O)=N)N=C(O)C(CCC(O)=N)N=C(O)C(CCC(O)=N)N=C(O)C(CCC(O)=O)N=C(O)C(CCC(O)=O)N=C(O)C(COP(O)(O)=O)N=C(O)C(CCC(O)=N)N=C(O)C(N)CC1=CC=CC=C1 BECPQYXYKAMYBN-UHFFFAOYSA-N 0.000 description 1
- 235000021240 caseins Nutrition 0.000 description 1
- 235000013339 cereals Nutrition 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 238000012364 cultivation method Methods 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 239000008367 deionised water Substances 0.000 description 1
- 229910021641 deionized water Inorganic materials 0.000 description 1
- 238000004332 deodorization Methods 0.000 description 1
- 235000013601 eggs Nutrition 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 230000035558 fertility Effects 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 230000009036 growth inhibition Effects 0.000 description 1
- 238000003306 harvesting Methods 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000011065 in-situ storage Methods 0.000 description 1
- 230000002401 inhibitory effect Effects 0.000 description 1
- 230000005764 inhibitory process Effects 0.000 description 1
- 239000002054 inoculum Substances 0.000 description 1
- 239000003621 irrigation water Substances 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 230000004060 metabolic process Effects 0.000 description 1
- 235000013336 milk Nutrition 0.000 description 1
- 239000008267 milk Substances 0.000 description 1
- 210000004080 milk Anatomy 0.000 description 1
- 229910000402 monopotassium phosphate Inorganic materials 0.000 description 1
- 235000019796 monopotassium phosphate Nutrition 0.000 description 1
- 235000021049 nutrient content Nutrition 0.000 description 1
- 239000011368 organic material Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 238000004806 packaging method and process Methods 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 230000035790 physiological processes and functions Effects 0.000 description 1
- 231100000572 poisoning Toxicity 0.000 description 1
- 230000000607 poisoning effect Effects 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- GNSKLFRGEWLPPA-UHFFFAOYSA-M potassium dihydrogen phosphate Chemical compound [K+].OP(O)([O-])=O GNSKLFRGEWLPPA-UHFFFAOYSA-M 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000004321 preservation Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- -1 small molecule sugar alcohols Chemical class 0.000 description 1
- 238000002791 soaking Methods 0.000 description 1
- 239000004016 soil organic matter Substances 0.000 description 1
- 241000894007 species Species 0.000 description 1
- 230000000087 stabilizing effect Effects 0.000 description 1
- 230000035882 stress Effects 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
- 238000003971 tillage Methods 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
- C12N1/20—Bacteria; Culture media therefor
-
- 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
-
- 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
- C05F17/20—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation using specific microorganisms or substances, e.g. enzymes, for activating or stimulating the treatment
-
- 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
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05G—MIXTURES 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
- C05G3/00—Mixtures of one or more fertilisers with additives not having a specially fertilising activity
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05G—MIXTURES 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
- C05G3/00—Mixtures of one or more fertilisers with additives not having a specially fertilising activity
- C05G3/60—Biocides or preservatives, e.g. disinfectants, pesticides or herbicides; Pest repellants or attractants
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05G—MIXTURES 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
- C05G3/00—Mixtures of one or more fertilisers with additives not having a specially fertilising activity
- C05G3/80—Soil conditioners
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
- C12N1/14—Fungi; Culture media therefor
- C12N1/16—Yeasts; Culture media therefor
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12R—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
- C12R2001/00—Microorganisms ; Processes using microorganisms
- C12R2001/01—Bacteria or Actinomycetales ; using bacteria or Actinomycetales
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12R—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
- C12R2001/00—Microorganisms ; Processes using microorganisms
- C12R2001/01—Bacteria or Actinomycetales ; using bacteria or Actinomycetales
- C12R2001/02—Acetobacter
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12R—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
- C12R2001/00—Microorganisms ; Processes using microorganisms
- C12R2001/01—Bacteria or Actinomycetales ; using bacteria or Actinomycetales
- C12R2001/07—Bacillus
- C12R2001/085—Bacillus cereus
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12R—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
- C12R2001/00—Microorganisms ; Processes using microorganisms
- C12R2001/01—Bacteria or Actinomycetales ; using bacteria or Actinomycetales
- C12R2001/07—Bacillus
- C12R2001/10—Bacillus licheniformis
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12R—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
- C12R2001/00—Microorganisms ; Processes using microorganisms
- C12R2001/01—Bacteria or Actinomycetales ; using bacteria or Actinomycetales
- C12R2001/07—Bacillus
- C12R2001/125—Bacillus subtilis ; Hay bacillus; Grass bacillus
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12R—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
- C12R2001/00—Microorganisms ; Processes using microorganisms
- C12R2001/01—Bacteria or Actinomycetales ; using bacteria or Actinomycetales
- C12R2001/225—Lactobacillus
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12R—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
- C12R2001/00—Microorganisms ; Processes using microorganisms
- C12R2001/645—Fungi ; Processes using fungi
-
- 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
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Health & Medical Sciences (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Biotechnology (AREA)
- Biochemistry (AREA)
- Wood Science & Technology (AREA)
- Microbiology (AREA)
- Genetics & Genomics (AREA)
- Zoology (AREA)
- Pest Control & Pesticides (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Tropical Medicine & Parasitology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Biomedical Technology (AREA)
- Mycology (AREA)
- General Health & Medical Sciences (AREA)
- Medicinal Chemistry (AREA)
- Virology (AREA)
- General Engineering & Computer Science (AREA)
- General Chemical & Material Sciences (AREA)
- Molecular Biology (AREA)
- Soil Sciences (AREA)
- Toxicology (AREA)
- Plant Pathology (AREA)
- Botany (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
- Fertilizers (AREA)
Abstract
Description
技术领域technical field
本发明属于环境保护领域中生物技术的使用,具体涉及一种促进水稻秸秆还田碳减排的微生物菌剂。The invention belongs to the use of biotechnology in the field of environmental protection, and in particular relates to a microbial bacterial agent for promoting the carbon emission reduction of rice straw returning to the field.
背景技术Background technique
秸秆还田是当今国内外上普遍重视的一种培肥、固碳、增产措施,不仅可减少秸秆露天焚烧所造成的大气污染问题,还能通过综合利用增加土壤有机质,改良土壤结构,使土壤孔隙度增加,实现耕地质量改善,土壤碳库提高,同时促进微生物活力和作物根系的发育,对稳粮增收、固碳增汇和污染防治具有重要意义。Straw returning to the field is a measure of fertilization, carbon sequestration, and production increase that is widely valued at home and abroad. It can not only reduce the air pollution caused by straw open-air burning, but also increase soil organic matter through comprehensive utilization, improve soil structure, and make soil The increase of porosity can improve the quality of arable land, increase the soil carbon pool, and at the same time promote the activity of microorganisms and the development of crop roots, which is of great significance for stabilizing grain income, increasing carbon sequestration and pollution prevention.
但目前研究来看,单纯的秸秆还田技术不仅存在着周期长、腐熟慢、费时费力等缺陷,还可能腐熟发酵产甲烷导致碳逸散,使最终固碳效果不稳定。而微生物菌剂,能充分利用微生物活性和分解能力,快速分解水稻秸秆中的纤维素、半纤维素、木质素,在物质转换和碳固定上具有良好的效益。因此,探索一种能高效降解作物秸秆,促进水稻秸秆还田碳减排的微生物菌株,对当下水稻秸秆还田技术的提高具有重要意义。However, according to the current research, the pure straw returning technology not only has defects such as long cycle, slow maturity, time-consuming and laborious, but also may lead to carbon dissipation due to methane production during decomposition and fermentation, making the final carbon sequestration effect unstable. The microbial agent can make full use of microbial activity and decomposition ability to quickly decompose cellulose, hemicellulose, and lignin in rice straw, and has good benefits in material transformation and carbon fixation. Therefore, it is of great significance to explore a microbial strain that can efficiently degrade crop straw and promote the carbon emission reduction of rice straw returning to the field to improve the current technology of rice straw returning to the field.
发明内容Contents of the invention
本发明针对水稻秸秆还田技术周期长、腐熟慢的缺陷,以及现有微生物菌剂固碳不稳定、碳减排效果差等问题,优选优势微生物菌株研发一种制备简便、功效稳定的复合微生物菌剂。多种活性微生物菌种良好的协同关系,可应对单一微生物菌剂效果不显著、活性不稳定、适应力差等问题,同时可在控制秸秆腐熟速度的基础上稳定固碳,解决当季秸秆中虫卵、带菌体等一些病虫害问题,保肥促进来年水稻生长发育,实现科学的水稻秸秆还田。Aiming at the defects of long cycle and slow maturity of rice straw returning technology, as well as the problems of unstable carbon fixation and poor carbon emission reduction effect of existing microbial agents, the present invention develops a compound microorganism with simple preparation and stable efficacy by optimizing superior microbial strains Bacteria. The good synergistic relationship of a variety of active microbial strains can deal with the problems of insignificant effect, unstable activity, and poor adaptability of a single microbial agent. Insect eggs, bacteria and other pest problems, fertilizer preservation can promote the growth and development of rice in the coming year, and realize scientific rice straw returning to the field.
本发明申请的关键点是一种促进水稻秸秆还田碳减排微生物菌剂的选配,选用具有强纤维素降解效果的多种芽孢杆菌作为复合菌剂主体,搭配乳酸菌、酵母菌、巴氏醋杆菌、光合细菌等有益菌,充分发挥微生物菌群在水稻秸秆还田的作用效果,返还土壤养分,节省肥料用量,不断改善土壤物理与生物性状,抑制产甲烷菌的活性并减少甲烷生成,实现水稻秸秆还田稳定固碳与资源化利用。此外,本发明的微生物菌剂还具备一定的抑制病原菌效果,并可使土壤及后续的农作物具备一定的抗病能力与抗逆性,提升土壤及农作物品质,发展“绿色农业”。The key point of the application of the present invention is the selection of a microbial agent for promoting rice straw returning to the field to reduce carbon emissions. A variety of bacillus with strong cellulose degradation effects are selected as the main body of the compound agent, and lactic acid bacteria, yeast, pasteurized Beneficial bacteria such as Acetobacter and photosynthetic bacteria give full play to the role of microbial flora in rice straw returning to the field, return soil nutrients, save fertilizer consumption, continuously improve soil physical and biological properties, inhibit the activity of methanogens and reduce methane production, Realize the stable carbon sequestration and resource utilization of rice straw returning to the field. In addition, the microbial agent of the present invention also has a certain effect of inhibiting pathogenic bacteria, and can make the soil and subsequent crops have certain disease resistance and stress resistance, improve the quality of soil and crops, and develop "green agriculture".
按照本发明,通过对水稻秸秆还田技术及固碳原理的研究,结合微生物技术及各类菌群的生理特性与习性,研发制备了一种促进水稻秸秆还田碳减排的复合微生物菌剂,其由多种芽孢杆菌及乳酸菌、酵母菌、巴氏醋杆菌、光合细菌等在土壤中常见的真菌与细菌复合而成,为固态菌剂,有效活菌数在70亿/克以上,可在常温(15℃以上)下快速升温、脱臭、脱水,降解秸秆中木质素、纤维素、半纤维,约一周时间左右完成腐熟。同时,减少甲烷、氨氮及有害有机酸的产生,提高土壤中的营养物质成分及碳含量,利于后续作物生长与长期供肥。本发明微生物菌剂主要活性成分及配比范围如下所示。According to the present invention, through the research on the technology of rice straw returning to the field and the principle of carbon fixation, combined with microbial technology and the physiological characteristics and habits of various types of bacteria, a composite microbial bacterial agent that promotes carbon emission reduction of rice straw returning to the field has been developed and prepared , which is composed of a variety of bacillus, lactic acid bacteria, yeast, Acetobacter pasteurianus, photosynthetic bacteria and other common fungi and bacteria in the soil. Rapid heating, deodorization, and dehydration at room temperature (above 15°C), degrades lignin, cellulose, and semi-fibers in straw, and completes decomposing in about a week. At the same time, it reduces the production of methane, ammonia nitrogen and harmful organic acids, increases the nutrient content and carbon content in the soil, and is conducive to the subsequent growth of crops and long-term fertilizer supply. The main active ingredients and proportioning range of the microbial agent of the present invention are as follows.
表1 复合微生物菌剂原料主要活性成分
本发明所述的微生物菌剂中,优选枯草芽孢杆菌、蜡状芽孢杆菌、地衣芽孢杆菌多类菌群,有效活菌数达30亿/克,可显著提高复合微生物菌剂腐解秸秆的效率,降解纤维素、糖类和淀粉等,缩短处理周期,使秸秆快速转变为营养丰富的有机物料,增加土壤全氮、有效磷、有机质和速效钾的含量,改善土壤肥力,促进作物生长并起有一定的抗病作用。Among the microbial agents of the present invention, Bacillus subtilis, Bacillus cereus, and Bacillus licheniformis are preferred, and the effective number of viable bacteria reaches 3 billion/g, which can significantly improve the efficiency of the compound microbial agent to decompose straw , degrade cellulose, sugar and starch, shorten the treatment cycle, quickly transform straw into nutrient-rich organic materials, increase soil total nitrogen, available phosphorus, organic matter and available potassium content, improve soil fertility, promote crop growth and play a role It has certain disease resistance.
本发明选配的乳酸菌可利用秸秆中的碳源,通过厌氧发酵产生乳酸,在发酵初期抑制其他有害菌的繁殖,同时促进复合微生物菌剂中的其他菌种发酵。此外,选配生命活力强、蛋白质含量高的酵母菌,协同分泌多种酶进行有机质发酵,加速水稻秸秆腐熟形成高品质肥;在后续水稻的自然生长过程中,酵母菌也可密集在作物根际周围产生酵母源生物刺激素与有机酸,增强作物的生理机能、非生物胁迫的抵抗力和品质的改善。The selected lactic acid bacteria of the present invention can use the carbon source in the straw to produce lactic acid through anaerobic fermentation, inhibit the reproduction of other harmful bacteria in the early stage of fermentation, and at the same time promote the fermentation of other bacterial species in the composite microbial agent. In addition, yeasts with strong vitality and high protein content are selected to secrete a variety of enzymes to ferment organic matter, and accelerate the maturity of rice straws to form high-quality fertilizers; during the subsequent natural growth of rice, yeasts can also be concentrated in crop roots Yeast-derived biostimulants and organic acids are produced around the environment to enhance the physiological functions of crops, the resistance to abiotic stress and the improvement of quality.
而巴氏醋杆菌作为好氧菌,可利用秸秆发酵前期菌种产生的代谢产物,进一步氧化分解,产生的小分子糖醇,氧化成乙酸等。在酸性环境下也能很好地生长,适合发酵后期pH下降后继续发酵,是秸秆发酵中后期主要的功能菌之一。As an aerobic bacterium, Acetobacter pasteurian can use the metabolites produced by the bacteria in the early stage of straw fermentation to further oxidize and decompose, and the small molecule sugar alcohols produced can be oxidized into acetic acid and the like. It can also grow well in an acidic environment, and is suitable for continuous fermentation after the pH drops in the late stage of fermentation. It is one of the main functional bacteria in the middle and late stages of straw fermentation.
本发明中的光合细菌,可在原位秸秆铺田插秧前,改善土壤因发酵腐熟、水面积水而造成的酸中毒及硫化氢中毒现象,为土壤及秸秆还田提供足量的氧气,促进有益菌及后续秧苗的生长发育。The photosynthetic bacteria in the present invention can improve the acidosis and hydrogen sulfide poisoning caused by fermentation and decomposing of the soil and water surface water before in-situ straw laying and transplanting, and provide sufficient oxygen for the soil and straw returning to the field to promote The growth and development of beneficial bacteria and subsequent seedlings.
本发明微生物菌剂,通过真菌和细菌的协同作用,可有效在整个发酵时期加速秸秆腐解,且所述菌种之间协同增效,无生长抑制等现象,利于秸秆还田。其次,多种芽孢杆菌代谢产物具有一定抑菌作用,可以加强对有害菌繁殖的抑制,保证复合微生物菌剂整个发酵周期中的代谢与生长。The microbial bacterial agent of the present invention can effectively accelerate straw decomposition during the whole fermentation period through the synergistic effect of fungi and bacteria, and the bacteria strains are synergistically synergistic without growth inhibition and the like, which is beneficial to straw returning to the field. Secondly, a variety of Bacillus metabolites have a certain antibacterial effect, which can strengthen the inhibition of the reproduction of harmful bacteria and ensure the metabolism and growth of the complex microbial agent throughout the fermentation cycle.
本发明所述微生物菌剂,制备过程简单,易于生产使用,以上所示菌种,均可于中国林业微生物菌种保藏管理中心或其他市场途径购买。经过研究与微生物菌剂配比效果探索,给出一种用于促进水稻秸秆还田碳减排的微生物菌剂优选配比为:The microbial agent of the present invention has a simple preparation process and is easy to produce and use. The strains shown above can be purchased from the China Forestry Microbial Strain Collection and Management Center or other market channels. After research and exploration of the ratio of microbial agents, an optimal ratio of microbial agents for promoting rice straw returning to the field for carbon emission reduction is given as follows:
表2 复合微生物菌剂主要活性成分优选配比
具体实施方式detailed description
实施例1Example 1
单一菌种的扩大扩繁培养,此处以多种芽孢杆菌、巴氏醋杆菌及酵母菌的培养为例进行说明。For the expansion and propagation of a single strain, the cultivation of a variety of Bacillus, Acetobacter pasteurianus and yeast is taken as an example to illustrate.
(1)多种芽孢杆菌的固体培养基组成:葡萄糖10.0g 、蛋白胨15.0g 、NaCl5.0g 、牛肉膏10.0g 、酵母膏5.0g、琼脂20.0g、蒸馏水1000mL。(PH=7.0-7.2)(1) Composition of solid medium for various bacillus: glucose 10.0g, peptone 15.0g, NaCl 5.0g, beef extract 10.0g, yeast extract 5.0g, agar 20.0g, distilled water 1000mL. (PH=7.0-7.2)
具体操作:15℃-40℃恒温箱内,将枯草芽孢杆菌/蜡状芽孢杆菌/地衣芽孢杆菌菌种在无菌条件下接种于营养琼脂培养基斜面上培养24小时,后无菌接种到营养肉汤培养基中,转速r=120-200r/min振荡培养24-48小时,最后接种到固体培养基上培养48小时。Specific operation: in an incubator at 15°C-40°C, inoculate the strains of Bacillus subtilis/Bacillus cereus/Bacillus licheniformis on the slant of nutrient agar medium under aseptic conditions for 24 hours, and then aseptically inoculate into the nutrient In the broth medium, the rotating speed r=120-200r/min shakes and cultivates for 24-48 hours, and finally inoculates on the solid medium and cultivates for 48 hours.
(2)巴氏醋杆菌的固体培养基组成:葡萄糖20.0g 、酵母膏10.0g、碳酸钙15.0g、琼脂20.0g。(PH=6.5-6.8)。(2) Composition of the solid medium for Acetobacter pasteurianus: 20.0 g of glucose, 10.0 g of yeast extract, 15.0 g of calcium carbonate, and 20.0 g of agar. (PH=6.5-6.8).
具体操作:将此培养基配方加入到1L蒸馏水或去离子水中(含氯量较高的自来水应敞口放置一天),搅拌加热煮沸至完全溶解,分装三角瓶121℃高压灭菌15分钟,冷却至30℃左右时按接种量5%接种斜面巴氏醋杆菌,转速r=120-200r/min振荡培养24-48小时,最后无菌接种到固体培养基上30℃恒温发酵培养48小时。Specific operation: Add this medium formula to 1L of distilled water or deionized water (tap water with high chlorine content should be left open for a day), stir and heat to boil until completely dissolved, then pack into triangular flasks and sterilize under high pressure at 121°C for 15 minutes. When cooled to about 30°C, inoculate Acetobacter slantii with 5% of the inoculum amount, rotate at r=120-200r/min and shake for 24-48 hours, and finally inoculate aseptically on solid medium for 48 hours of constant temperature fermentation at 30°C.
(3)酵母菌的固体培养基组成:葡萄糖50.0g、酸水解酪蛋白5.0g、KH2PO40.5g、KCl0.5g、CaCl20.2g、MgSO40.2g、琼脂20g。(PH=5.5)(3) Composition of solid medium for yeast: 50.0g glucose, 5.0g acid hydrolyzed casein, 0.5g KH2PO, 0.5g KCl, 0.2g CaCl, 0.2g MgSO4, 20g agar. (PH=5.5)
具体操作:12℃-36℃恒温箱内,将酵母菌菌种在无菌条件下接种于酵母膏胨葡萄糖营养琼脂培养基斜面上培养24小时,后无菌接种到豆浆中,转速r=120-200r/min振荡培养24-48小时,最后无菌接种到固体培养基上培养48小时。Specific operation: in an incubator at 12°C-36°C, inoculate yeast strains on the slant of yeast extract peptone glucose nutrient agar medium for 24 hours under aseptic conditions, and then aseptically inoculate them into soybean milk at a speed of r=120 Shake culture at -200r/min for 24-48 hours, and finally inoculate aseptically on solid medium for 48 hours.
上述营养琼脂培养基的成分为蛋白胨10g,牛肉膏3g,氯化钠5g,琼脂15g,加水至1000ml,调PH为7.2,121℃高压灭菌15min。The above nutrient agar medium consists of 10g of peptone, 3g of beef extract, 5g of sodium chloride, 15g of agar, add water to 1000ml, adjust the pH to 7.2, and autoclave at 121°C for 15min.
上述营养肉汤培养基的成分为蛋白胨10g ,牛肉粉3g,氯化钠5g,加水至1000ml,调PH为7.2,121℃高压灭菌15 min。The above nutrient broth medium consists of 10g of peptone, 3g of beef powder, 5g of sodium chloride, adding water to 1000ml, adjusting the pH to 7.2, and autoclaving at 121°C for 15 minutes.
实施例2Example 2
(1)复合芽孢杆菌培养(1) Composite Bacillus culture
将实施例1(1)中三类杆菌按照质量比1:1:1的比例混合菌种,并于复合芽孢杆菌培养基中扩大培养后计数。其中培养基组成为:可溶性淀粉10.0g、蛋白胨10.0g、酵母膏5.0g、KH2PO4 3.0g、NaCl 0.5g 、MgSO40.1g。(PH=7.0-7.4)The three types of bacteria in Example 1 (1) were mixed according to the mass ratio of 1:1:1, and were counted after expanding culture in the compound bacillus culture medium. The culture medium consists of: 10.0g soluble starch, 10.0g peptone, 5.0g yeast extract, 3.0g KH2PO4, 0.5g NaCl, 0.1g MgSO4. (PH=7.0-7.4)
(2)复合微生物制剂(2) Compound microbial preparations
将各大菌种分别在对应的培养基中活化并进行增菌扩培后,按照表2重量百分比混合(枯草芽孢杆菌15%、蜡状芽孢杆菌15%、地衣芽孢杆菌15%、乳酸菌10%、酵母菌10%、巴氏醋杆菌15%、光合细菌 20%),搅拌均匀并接种复合菌种10g于发酵罐中培养48-72小时,制成复合强化微生物菌剂。其中,发酵罐中培养基配方:葡萄糖20.0g、红糖15.0g、可溶性淀粉10.0g、蛋白胨10.0g、牛肉膏5.0g、酵母膏3.0g、KH2PO42.0g、K2HPO41.0g、琼脂15.0g、蒸馏水1000mL,121℃灭菌20min。After activating the various strains in the corresponding medium and carrying out the enrichment and expansion, they were mixed according to the weight percentage in Table 2 (15% of Bacillus subtilis, 15% of Bacillus cereus, 15% of Bacillus licheniformis, 10% of lactic acid bacteria , 10% yeast, 15% Acetobacter pasteurianus, 20% photosynthetic bacteria), stir evenly and inoculate 10g of composite bacteria in a fermenter for 48-72 hours to make a composite enhanced microbial agent. Among them, the medium formula in the fermenter: 20.0g glucose, 15.0g brown sugar, 10.0g soluble starch, 10.0g peptone, 5.0g beef extract, 3.0g yeast extract, 2.0g KH2PO, 41.0g K2HPO, 15.0g agar, 1000mL distilled water , sterilized at 121°C for 20 minutes.
将培养后的微生物菌剂混合物进行常温干燥、粉碎后,加入适量石灰进行包装,即为复合微生物制剂,其有效活菌数可达70亿/克以上,在阴凉通风处密封避光保存可存6~12个月,一个月内使用效果最佳。After the cultured microbial agent mixture is dried and crushed at room temperature, then an appropriate amount of lime is added for packaging, which is a compound microbial agent, and the effective number of viable bacteria can reach more than 7 billion/g. 6-12 months, the effect is best when used within one month.
实施例3Example 3
与实施例3不同的是,复合菌种比例为:枯草芽孢杆菌15%、蜡状芽孢杆菌15%、地衣芽孢杆菌15%、乳酸菌10%、酵母菌10%、巴氏醋杆菌20%、光合细菌15%The difference from Example 3 is that the proportion of composite bacteria is: Bacillus subtilis 15%, Bacillus cereus 15%, Bacillus licheniformis 15%, lactic acid bacteria 10%, yeast 10%, Acetobacter pasteurianus 20%, photosynthetic Bacteria 15%
实施例4Example 4
与实施例3不同的是,复合菌种比例为:枯草芽孢杆菌15%、蜡状芽孢杆菌15%、地衣芽孢杆菌15%、乳酸菌10%、酵母菌10%、巴氏醋杆菌10%、光合细菌25%The difference from Example 3 is that the proportion of composite bacteria is: Bacillus subtilis 15%, Bacillus cereus 15%, Bacillus licheniformis 15%, lactic acid bacteria 10%, yeast 10%, Acetobacter pasteurianus 10%, photosynthetic Bacteria 25%
实施例5Example 5
将本发明实施例2、3、4中复合微生物制剂用于水稻秸秆还田,可掺混秸秆平铺或堆腐还田,也可以采用留茬旋耕的方式,本实施例5以直接原地平铺覆盖水稻秸秆还田为例进行微生物菌剂使用方式说明。The composite microbial preparations in Examples 2, 3, and 4 of the present invention are used for rice straw returning to the field, and the straw can be mixed and spread or piled up and returned to the field, or the method of rotary tillage with stubble can be used. In Example 5, the direct original The use of microbial agents will be explained by taking the rice straw covered with the ground and returning it to the field as an example.
(1)平铺秸秆(1) Tiling the straw
在收割水稻之后,将水稻秸秆粉碎成5-8的碎段均匀平铺在田面上,避免碎草成堆。After harvesting the rice, crush the rice stalks into 5-8 pieces and spread them evenly on the field to avoid piles of broken grass.
(2)施菌施肥(2) Bacteria fertilization
秸秆铺好后,按每亩2公斤微生物菌剂的用量与适量泥土或底肥拌和均匀后撒施到铺好秸秆的田内,并按高产标准施肥要求基肥,同时,每亩加施农家肥100-200公斤或尿素3-5公斤或碳铵10-20公斤来调节碳氮比,以避免微生物在分解过程中与后茬作物幼苗争夺速效氮素的现象,影响后茬作物正常生长。After the straw is laid, mix the amount of 2 kg of microbial agent per mu with an appropriate amount of soil or base fertilizer and spread it evenly on the field where the straw is laid, and fertilize the base fertilizer according to the high-yield standard. At the same time, add farmyard manure 100- 200 kg or 3-5 kg of urea or 10-20 kg of ammonium bicarbonate to adjust the carbon-nitrogen ratio to avoid the phenomenon that microorganisms compete with the crop seedlings for available nitrogen during the decomposition process and affect the normal growth of crops.
(3)灭茬灌水(3) Stubble irrigation
采用机械或人工拍打压秆进行灭茬,使水稻秸秆沉降到地表土壤内,及时耙实,防止秸秆泡水后浮起,以利保墒。第一次灌水7-10cm深,使秸秆充分吸足水分,快速升温发酵、腐烂分解,实现稳定固碳。Mechanically or manually beat the stalks for stubble removal, so that the rice stalks will settle into the surface soil, and raked in time to prevent the stalks from floating after soaking in water, so as to preserve moisture. The first irrigation is 7-10cm deep, so that the straw can fully absorb water, quickly heat up for fermentation, rot and decompose, and achieve stable carbon fixation.
(4)播种与管理(4) Sowing and management
秸秆完全腐熟后翻耕平整,灌水深1-3cm将浸种后的水稻种子均匀撒播于地表(或进行插秧),播种量比常规栽培法增加10%左右。秧苗培育期间,科学合理的控制稻田水量,建立的浅、干、湿灵活调节的稻田CH4低排放的水分管理模式,以减少秸秆还田的碳排放;其他施肥及病虫草害防治按常规方法正常进行。After the straw is completely decomposed, it is plowed and leveled, and the soaked rice seeds are evenly spread on the ground (or transplanted) with irrigation water depth of 1-3cm. The sowing amount is about 10% higher than that of conventional cultivation methods. During the cultivation of seedlings, scientifically and rationally control the amount of water in the paddy field, and establish a shallow, dry, and wet flexible adjustment of paddy field CH4 low emission water management mode to reduce carbon emissions from straw returning to the field; other fertilization and pest and weed control are normal conduct.
实施例5中不同配比的微生物菌剂作用效果存在略微差异,但都可以在7天左右实现水稻秸秆完全腐熟,期间的甲烷、硫化氢等物质的产生大幅减少,有效促进了水稻秸秆还田的碳减排,实现土壤固碳与改良;后续秧苗的生长也更加壮实,受虫害影响率有所降低,水稻品质更高。In Example 5, there are slight differences in the effects of microbial agents with different proportions, but they can all achieve complete decomposition of rice straw in about 7 days, during which the production of methane, hydrogen sulfide and other substances is greatly reduced, which effectively promotes the return of rice straw to the field. carbon emission reduction, soil carbon sequestration and improvement; the growth of subsequent seedlings is also stronger, the rate of impact by insect pests is reduced, and the quality of rice is higher.
Claims (3)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202211278840.5A CN115491331A (en) | 2022-10-19 | 2022-10-19 | A microbial agent that promotes carbon emission reduction in rice straw returning to the field |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202211278840.5A CN115491331A (en) | 2022-10-19 | 2022-10-19 | A microbial agent that promotes carbon emission reduction in rice straw returning to the field |
Publications (1)
Publication Number | Publication Date |
---|---|
CN115491331A true CN115491331A (en) | 2022-12-20 |
Family
ID=84473572
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202211278840.5A Pending CN115491331A (en) | 2022-10-19 | 2022-10-19 | A microbial agent that promotes carbon emission reduction in rice straw returning to the field |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN115491331A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN116254117A (en) * | 2023-05-16 | 2023-06-13 | 东北农业大学 | A rice field methane emission inhibitor and method for reducing rice field methane emission |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20140352376A1 (en) * | 2013-05-28 | 2014-12-04 | BiOWiSH Technologies, Inc. | Fertilizer compositions methods of making and using same |
CN106278537A (en) * | 2016-07-25 | 2017-01-04 | 昆山工研院华科生物高分子材料研究所有限公司 | A kind of method of straw-returning |
CN107502582A (en) * | 2017-10-11 | 2017-12-22 | 杨建设 | A kind of organic matter decomposing inoculant and preparation method thereof |
CN112458000A (en) * | 2019-09-06 | 2021-03-09 | 中科元生生物技术(天津)有限公司 | Compound microbial agent for returning straws to field and preparation method and application thereof |
-
2022
- 2022-10-19 CN CN202211278840.5A patent/CN115491331A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20140352376A1 (en) * | 2013-05-28 | 2014-12-04 | BiOWiSH Technologies, Inc. | Fertilizer compositions methods of making and using same |
CN106278537A (en) * | 2016-07-25 | 2017-01-04 | 昆山工研院华科生物高分子材料研究所有限公司 | A kind of method of straw-returning |
CN107502582A (en) * | 2017-10-11 | 2017-12-22 | 杨建设 | A kind of organic matter decomposing inoculant and preparation method thereof |
CN112458000A (en) * | 2019-09-06 | 2021-03-09 | 中科元生生物技术(天津)有限公司 | Compound microbial agent for returning straws to field and preparation method and application thereof |
Non-Patent Citations (1)
Title |
---|
韩梦颖 等: "降解秸秆微生物及秸秆腐熟剂的研究进展", 《南方农业学报》, vol. 48, no. 6, 10 July 2017 (2017-07-10), pages 1024 - 1030 * |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN116254117A (en) * | 2023-05-16 | 2023-06-13 | 东北农业大学 | A rice field methane emission inhibitor and method for reducing rice field methane emission |
CN116254117B (en) * | 2023-05-16 | 2023-07-21 | 东北农业大学 | Rice field methane emission inhibitor and method for reducing rice field methane emission |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN101497870B (en) | Microbial complex bacterial agent and use thereof | |
CN103194407B (en) | Straw-decomposition composite microbial preparation and preparation method thereof | |
CN101671633B (en) | Antagonist bacteria for controlling Verticillium wilt in continuous cropping cotton and its microbial organic fertilizer | |
CN109400372B (en) | Biochar soil improvement organic fertilizer and preparation method thereof | |
CN103168668A (en) | Fruit and vegetable seedling culturing substrate prepared by utilizing agricultural wastes | |
CN109679860A (en) | A kind of composite bacteria agent and the preparation method and application thereof for the processing of gardens green waste | |
CN105684847A (en) | Seedling cultivation substrate special for watermelons and preparation method thereof | |
CN106554240A (en) | A kind of crops soil improving agent for one-crop succession and preparation method thereof | |
CN108863483A (en) | Quick animal excretion compost method | |
CN107580818B (en) | A kind of integrated approach of soil conditioning and reparation | |
CN111357612B (en) | Composite microbial matrix for watermelon planting and preparation method and application thereof | |
CN107325990A (en) | A kind of complex microorganism decomposing agent and its purposes for tobacco cultivation | |
CN108821875A (en) | A kind of preparation method of high-activity microorganism fertilizer | |
CN110628675A (en) | Straw field-returning decomposition agent and preparation method thereof | |
CN108191565A (en) | For improveing the compost product of tobacco-growing soil and its application | |
CN102154159A (en) | Antagonistic bacteria for preventing and controlling tomato root-knot nematodes and microorganism organic fertilizer produced by same | |
CN110330370A (en) | While a kind of turf biological organic fertilizer and its preparation method and application containing trichoderma and bacillus amyloliquefaciens | |
CN106007824B (en) | Composite bacterial fertilizer and preparation method and application thereof | |
US20240002308A1 (en) | Soil-structure improving bio-organic fertilizer and preparation method thereof | |
CN112430163B (en) | A kind of biological fertilizer for relieving the continuous cropping obstacle of sand-pressed watermelon | |
CN110066194A (en) | Novel more bacterium composite microbe fertilizers of one kind and its preparation method and application | |
CN103351188A (en) | Preparation method of agricultural organic fertilizer by treating pure straws as raw material | |
CN103173387B (en) | Growth-promoting bacteria for facilitating growth of rape and microbial organic fertilizer | |
CN115491331A (en) | A microbial agent that promotes carbon emission reduction in rice straw returning to the field | |
CN107176855B (en) | Bio-organic fertilizer and application thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20221220 |
|
RJ01 | Rejection of invention patent application after publication |