JP2020141564A - Plant growth promoting agent and method for producing plant growth promoting agent - Google Patents
Plant growth promoting agent and method for producing plant growth promoting agent Download PDFInfo
- Publication number
- JP2020141564A JP2020141564A JP2019038319A JP2019038319A JP2020141564A JP 2020141564 A JP2020141564 A JP 2020141564A JP 2019038319 A JP2019038319 A JP 2019038319A JP 2019038319 A JP2019038319 A JP 2019038319A JP 2020141564 A JP2020141564 A JP 2020141564A
- Authority
- JP
- Japan
- Prior art keywords
- plant growth
- phylum
- growth promoter
- microorganisms
- contained
- 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.)
- Granted
Links
- 230000008635 plant growth Effects 0.000 title claims abstract description 121
- 238000004519 manufacturing process Methods 0.000 title claims abstract description 22
- 230000001737 promoting effect Effects 0.000 title abstract description 17
- 244000005700 microbiome Species 0.000 claims abstract description 107
- 239000010871 livestock manure Substances 0.000 claims abstract description 53
- 241001142109 Chloroflexi Species 0.000 claims abstract description 14
- 241001265526 Gemmatimonadetes <phylum> Species 0.000 claims abstract description 13
- 241001261005 Verrucomicrobia Species 0.000 claims abstract description 12
- 241000605059 Bacteroidetes Species 0.000 claims abstract description 10
- 239000007952 growth promoter Substances 0.000 claims description 104
- 239000007788 liquid Substances 0.000 claims description 49
- 238000005273 aeration Methods 0.000 claims description 48
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 36
- 229910052757 nitrogen Inorganic materials 0.000 claims description 18
- 229910052799 carbon Inorganic materials 0.000 claims description 17
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 claims description 15
- 229910052698 phosphorus Inorganic materials 0.000 claims description 15
- 239000011574 phosphorus Substances 0.000 claims description 15
- 239000011591 potassium Substances 0.000 claims description 14
- 229910052700 potassium Inorganic materials 0.000 claims description 14
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 claims description 13
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 12
- FWMNVWWHGCHHJJ-SKKKGAJSSA-N 4-amino-1-[(2r)-6-amino-2-[[(2r)-2-[[(2r)-2-[[(2r)-2-amino-3-phenylpropanoyl]amino]-3-phenylpropanoyl]amino]-4-methylpentanoyl]amino]hexanoyl]piperidine-4-carboxylic acid Chemical compound C([C@H](C(=O)N[C@H](CC(C)C)C(=O)N[C@H](CCCCN)C(=O)N1CCC(N)(CC1)C(O)=O)NC(=O)[C@H](N)CC=1C=CC=CC=1)C1=CC=CC=C1 FWMNVWWHGCHHJJ-SKKKGAJSSA-N 0.000 claims description 8
- 239000007787 solid Substances 0.000 claims description 7
- 239000002773 nucleotide Substances 0.000 claims description 5
- 125000003729 nucleotide group Chemical group 0.000 claims description 5
- 238000007696 Kjeldahl method Methods 0.000 claims description 3
- 239000002002 slurry Substances 0.000 claims description 3
- 239000002994 raw material Substances 0.000 abstract description 6
- 210000003608 fece Anatomy 0.000 description 34
- 241000196324 Embryophyta Species 0.000 description 20
- 108020004414 DNA Proteins 0.000 description 18
- 239000003337 fertilizer Substances 0.000 description 12
- 239000000203 mixture Substances 0.000 description 11
- 238000003753 real-time PCR Methods 0.000 description 11
- 235000007688 Lycopersicon esculentum Nutrition 0.000 description 10
- 240000003768 Solanum lycopersicum Species 0.000 description 10
- 239000002361 compost Substances 0.000 description 10
- 230000000694 effects Effects 0.000 description 10
- 238000000034 method Methods 0.000 description 10
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 9
- 239000000047 product Substances 0.000 description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 9
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 8
- 238000004458 analytical method Methods 0.000 description 8
- 238000006243 chemical reaction Methods 0.000 description 8
- 230000012010 growth Effects 0.000 description 8
- 241000283690 Bos taurus Species 0.000 description 7
- 244000233513 Brassica perviridis Species 0.000 description 7
- 239000000243 solution Substances 0.000 description 7
- 238000012360 testing method Methods 0.000 description 7
- 241000606125 Bacteroides Species 0.000 description 6
- 108091028043 Nucleic acid sequence Proteins 0.000 description 6
- 238000012408 PCR amplification Methods 0.000 description 6
- 241000207196 Verrucomicrobium Species 0.000 description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 6
- 239000005416 organic matter Substances 0.000 description 6
- 229910052760 oxygen Inorganic materials 0.000 description 6
- 239000001301 oxygen Substances 0.000 description 6
- 239000000126 substance Substances 0.000 description 6
- 239000006228 supernatant Substances 0.000 description 6
- 102000053602 DNA Human genes 0.000 description 5
- 241000287828 Gallus gallus Species 0.000 description 5
- 241000192142 Proteobacteria Species 0.000 description 5
- 235000013330 chicken meat Nutrition 0.000 description 5
- 238000005259 measurement Methods 0.000 description 5
- 108020004465 16S ribosomal RNA Proteins 0.000 description 4
- 241000580482 Acidobacteria Species 0.000 description 4
- 241000894006 Bacteria Species 0.000 description 4
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 4
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 4
- 238000004925 denaturation Methods 0.000 description 4
- 230000036425 denaturation Effects 0.000 description 4
- 230000035784 germination Effects 0.000 description 4
- 235000015097 nutrients Nutrition 0.000 description 4
- 239000002689 soil Substances 0.000 description 4
- 238000003860 storage Methods 0.000 description 4
- GUAHPAJOXVYFON-ZETCQYMHSA-N (8S)-8-amino-7-oxononanoic acid zwitterion Chemical compound C[C@H](N)C(=O)CCCCCC(O)=O GUAHPAJOXVYFON-ZETCQYMHSA-N 0.000 description 3
- 241000191366 Chlorobium Species 0.000 description 3
- 241000192733 Chloroflexus Species 0.000 description 3
- JVMRPSJZNHXORP-UHFFFAOYSA-N ON=O.ON=O.ON=O.N Chemical compound ON=O.ON=O.ON=O.N JVMRPSJZNHXORP-UHFFFAOYSA-N 0.000 description 3
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 3
- MMDJDBSEMBIJBB-UHFFFAOYSA-N [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] Chemical compound [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] MMDJDBSEMBIJBB-UHFFFAOYSA-N 0.000 description 3
- 238000002835 absorbance Methods 0.000 description 3
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 3
- 239000011324 bead Substances 0.000 description 3
- 239000003795 chemical substances by application Substances 0.000 description 3
- 238000009313 farming Methods 0.000 description 3
- 230000000813 microbial effect Effects 0.000 description 3
- 238000011084 recovery Methods 0.000 description 3
- 230000002829 reductive effect Effects 0.000 description 3
- 238000012163 sequencing technique Methods 0.000 description 3
- 241000894007 species Species 0.000 description 3
- CIWBSHSKHKDKBQ-JLAZNSOCSA-N Ascorbic acid Chemical compound OC[C@H](O)[C@H]1OC(=O)C(O)=C1O CIWBSHSKHKDKBQ-JLAZNSOCSA-N 0.000 description 2
- HEDRZPFGACZZDS-UHFFFAOYSA-N Chloroform Chemical compound ClC(Cl)Cl HEDRZPFGACZZDS-UHFFFAOYSA-N 0.000 description 2
- 206010021143 Hypoxia Diseases 0.000 description 2
- KFZMGEQAYNKOFK-UHFFFAOYSA-N Isopropanol Chemical compound CC(C)O KFZMGEQAYNKOFK-UHFFFAOYSA-N 0.000 description 2
- ISWSIDIOOBJBQZ-UHFFFAOYSA-N Phenol Chemical compound OC1=CC=CC=C1 ISWSIDIOOBJBQZ-UHFFFAOYSA-N 0.000 description 2
- 241000230332 Prosthecobacter Species 0.000 description 2
- 238000000137 annealing Methods 0.000 description 2
- OPTASPLRGRRNAP-UHFFFAOYSA-N cytosine Chemical compound NC=1C=CNC(=O)N=1 OPTASPLRGRRNAP-UHFFFAOYSA-N 0.000 description 2
- 239000002552 dosage form Substances 0.000 description 2
- UYTPUPDQBNUYGX-UHFFFAOYSA-N guanine Chemical compound O=C1NC(N)=NC2=C1N=CN2 UYTPUPDQBNUYGX-UHFFFAOYSA-N 0.000 description 2
- 239000003501 hydroponics Substances 0.000 description 2
- 239000003112 inhibitor Substances 0.000 description 2
- 230000002401 inhibitory effect Effects 0.000 description 2
- PHTQWCKDNZKARW-UHFFFAOYSA-N isoamylol Chemical compound CC(C)CCO PHTQWCKDNZKARW-UHFFFAOYSA-N 0.000 description 2
- JVTAAEKCZFNVCJ-UHFFFAOYSA-N lactic acid Chemical compound CC(O)C(O)=O JVTAAEKCZFNVCJ-UHFFFAOYSA-N 0.000 description 2
- 244000144972 livestock Species 0.000 description 2
- 239000003895 organic fertilizer Substances 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 239000002096 quantum dot Substances 0.000 description 2
- 239000011780 sodium chloride Substances 0.000 description 2
- 238000009331 sowing Methods 0.000 description 2
- 239000011550 stock solution Substances 0.000 description 2
- 230000002195 synergetic effect Effects 0.000 description 2
- RWQNBRDOKXIBIV-UHFFFAOYSA-N thymine Chemical compound CC1=CNC(=O)NC1=O RWQNBRDOKXIBIV-UHFFFAOYSA-N 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- 239000002023 wood Substances 0.000 description 2
- ZCUQOPGIJRGJDA-UHFFFAOYSA-N 1-naphthalen-1-ylethane-1,2-diamine Chemical compound C1=CC=C2C(C(N)CN)=CC=CC2=C1 ZCUQOPGIJRGJDA-UHFFFAOYSA-N 0.000 description 1
- QKNYBSVHEMOAJP-UHFFFAOYSA-N 2-amino-2-(hydroxymethyl)propane-1,3-diol;hydron;chloride Chemical compound Cl.OCC(N)(CO)CO QKNYBSVHEMOAJP-UHFFFAOYSA-N 0.000 description 1
- VRZJGENLTNRAIG-UHFFFAOYSA-N 4-[4-(dimethylamino)phenyl]iminonaphthalen-1-one Chemical compound C1=CC(N(C)C)=CC=C1N=C1C2=CC=CC=C2C(=O)C=C1 VRZJGENLTNRAIG-UHFFFAOYSA-N 0.000 description 1
- HVBSAKJJOYLTQU-UHFFFAOYSA-N 4-aminobenzenesulfonic acid Chemical compound NC1=CC=C(S(O)(=O)=O)C=C1 HVBSAKJJOYLTQU-UHFFFAOYSA-N 0.000 description 1
- 229930024421 Adenine Natural products 0.000 description 1
- GFFGJBXGBJISGV-UHFFFAOYSA-N Adenine Chemical compound NC1=NC=NC2=C1N=CN2 GFFGJBXGBJISGV-UHFFFAOYSA-N 0.000 description 1
- 241000633183 Anaerolinea Species 0.000 description 1
- 241000253548 Ardenticatena Species 0.000 description 1
- 241000606124 Bacteroides fragilis Species 0.000 description 1
- 241001220441 Bacteroides plebeius Species 0.000 description 1
- 241001141113 Bacteroidia Species 0.000 description 1
- 241000920564 Caldilinea aerophila Species 0.000 description 1
- 241001358012 Caldilinea tarbellica Species 0.000 description 1
- 241000283707 Capra Species 0.000 description 1
- LZZYPRNAOMGNLH-UHFFFAOYSA-M Cetrimonium bromide Chemical compound [Br-].CCCCCCCCCCCCCCCC[N+](C)(C)C LZZYPRNAOMGNLH-UHFFFAOYSA-M 0.000 description 1
- 241001425699 Chlorobia Species 0.000 description 1
- 102000016928 DNA-directed DNA polymerase Human genes 0.000 description 1
- 108010014303 DNA-directed DNA polymerase Proteins 0.000 description 1
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 description 1
- 108010067770 Endopeptidase K Proteins 0.000 description 1
- JOYRKODLDBILNP-UHFFFAOYSA-N Ethyl urethane Chemical compound CCOC(N)=O JOYRKODLDBILNP-UHFFFAOYSA-N 0.000 description 1
- 241000230562 Flavobacteriia Species 0.000 description 1
- 241000719958 Gemmatimonas Species 0.000 description 1
- 241000719997 Gemmatimonas aurantiaca Species 0.000 description 1
- 241001636242 Gemmatimonas phototrophica Species 0.000 description 1
- 241001629562 Gemmatirosa kalamazoonesis Species 0.000 description 1
- 241001217144 Haloferula Species 0.000 description 1
- 241001430082 Ktedonobacter Species 0.000 description 1
- 241000869457 Longimicrobium Species 0.000 description 1
- 241000951861 Longimicrobium terrae Species 0.000 description 1
- 241000741587 Luteolibacter Species 0.000 description 1
- 241001465754 Metazoa Species 0.000 description 1
- 108091034117 Oligonucleotide Proteins 0.000 description 1
- 241000777895 Opitutus Species 0.000 description 1
- 240000007594 Oryza sativa Species 0.000 description 1
- 235000007164 Oryza sativa Nutrition 0.000 description 1
- 241001494479 Pecora Species 0.000 description 1
- 241000741589 Persicirhabdus Species 0.000 description 1
- 241000425347 Phyla <beetle> Species 0.000 description 1
- 241000741591 Roseibacillus Species 0.000 description 1
- 241000502378 Roseimicrobium Species 0.000 description 1
- 240000004808 Saccharomyces cerevisiae Species 0.000 description 1
- 241000191112 Saprospira Species 0.000 description 1
- 239000005708 Sodium hypochlorite Substances 0.000 description 1
- 241000203745 Sphaerobacter thermophilus Species 0.000 description 1
- 241000230565 Sphingobacteriia Species 0.000 description 1
- 241000282887 Suidae Species 0.000 description 1
- 241000356651 Thermoflexus Species 0.000 description 1
- 241000828395 Thermogemmatispora foliorum Species 0.000 description 1
- 241000828397 Thermogemmatispora onikobensis Species 0.000 description 1
- 241000588679 Thermomicrobium Species 0.000 description 1
- 241000589017 Thermomicrobium roseum Species 0.000 description 1
- 241000343968 Thermosporothrix Species 0.000 description 1
- 239000007984 Tris EDTA buffer Substances 0.000 description 1
- 239000007983 Tris buffer Substances 0.000 description 1
- 241001183192 Verrucomicrobiae Species 0.000 description 1
- JLCPHMBAVCMARE-UHFFFAOYSA-N [3-[[3-[[3-[[3-[[3-[[3-[[3-[[3-[[3-[[3-[[3-[[5-(2-amino-6-oxo-1H-purin-9-yl)-3-[[3-[[3-[[3-[[3-[[3-[[5-(2-amino-6-oxo-1H-purin-9-yl)-3-[[5-(2-amino-6-oxo-1H-purin-9-yl)-3-hydroxyoxolan-2-yl]methoxy-hydroxyphosphoryl]oxyoxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(5-methyl-2,4-dioxopyrimidin-1-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(6-aminopurin-9-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(6-aminopurin-9-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(6-aminopurin-9-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(6-aminopurin-9-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxyoxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(5-methyl-2,4-dioxopyrimidin-1-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(4-amino-2-oxopyrimidin-1-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(5-methyl-2,4-dioxopyrimidin-1-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(5-methyl-2,4-dioxopyrimidin-1-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(6-aminopurin-9-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(6-aminopurin-9-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(4-amino-2-oxopyrimidin-1-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(4-amino-2-oxopyrimidin-1-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(4-amino-2-oxopyrimidin-1-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(6-aminopurin-9-yl)oxolan-2-yl]methoxy-hydroxyphosphoryl]oxy-5-(4-amino-2-oxopyrimidin-1-yl)oxolan-2-yl]methyl [5-(6-aminopurin-9-yl)-2-(hydroxymethyl)oxolan-3-yl] hydrogen phosphate Polymers Cc1cn(C2CC(OP(O)(=O)OCC3OC(CC3OP(O)(=O)OCC3OC(CC3O)n3cnc4c3nc(N)[nH]c4=O)n3cnc4c3nc(N)[nH]c4=O)C(COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3COP(O)(=O)OC3CC(OC3CO)n3cnc4c(N)ncnc34)n3ccc(N)nc3=O)n3cnc4c(N)ncnc34)n3ccc(N)nc3=O)n3ccc(N)nc3=O)n3ccc(N)nc3=O)n3cnc4c(N)ncnc34)n3cnc4c(N)ncnc34)n3cc(C)c(=O)[nH]c3=O)n3cc(C)c(=O)[nH]c3=O)n3ccc(N)nc3=O)n3cc(C)c(=O)[nH]c3=O)n3cnc4c3nc(N)[nH]c4=O)n3cnc4c(N)ncnc34)n3cnc4c(N)ncnc34)n3cnc4c(N)ncnc34)n3cnc4c(N)ncnc34)O2)c(=O)[nH]c1=O JLCPHMBAVCMARE-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 229960000643 adenine Drugs 0.000 description 1
- 238000000246 agarose gel electrophoresis Methods 0.000 description 1
- APUPEJJSWDHEBO-UHFFFAOYSA-P ammonium molybdate Chemical compound [NH4+].[NH4+].[O-][Mo]([O-])(=O)=O APUPEJJSWDHEBO-UHFFFAOYSA-P 0.000 description 1
- 235000018660 ammonium molybdate Nutrition 0.000 description 1
- 239000011609 ammonium molybdate Substances 0.000 description 1
- 229940010552 ammonium molybdate Drugs 0.000 description 1
- 235000010323 ascorbic acid Nutrition 0.000 description 1
- 229960005070 ascorbic acid Drugs 0.000 description 1
- 239000011668 ascorbic acid Substances 0.000 description 1
- 238000001479 atomic absorption spectroscopy Methods 0.000 description 1
- RRKTZKIUPZVBMF-IBTVXLQLSA-N brucine Chemical compound O([C@@H]1[C@H]([C@H]2C3)[C@@H]4N(C(C1)=O)C=1C=C(C(=CC=11)OC)OC)CC=C2CN2[C@@H]3[C@]41CC2 RRKTZKIUPZVBMF-IBTVXLQLSA-N 0.000 description 1
- RRKTZKIUPZVBMF-UHFFFAOYSA-N brucine Natural products C1=2C=C(OC)C(OC)=CC=2N(C(C2)=O)C3C(C4C5)C2OCC=C4CN2C5C31CC2 RRKTZKIUPZVBMF-UHFFFAOYSA-N 0.000 description 1
- 238000004364 calculation method Methods 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 238000007621 cluster analysis Methods 0.000 description 1
- 230000000295 complement effect Effects 0.000 description 1
- 238000009264 composting Methods 0.000 description 1
- 238000012790 confirmation Methods 0.000 description 1
- 229940104302 cytosine Drugs 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 239000008367 deionised water Substances 0.000 description 1
- 229910021641 deionized water Inorganic materials 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 239000003085 diluting agent Substances 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 230000035558 fertility Effects 0.000 description 1
- 230000004720 fertilization Effects 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- -1 for example Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 230000003054 hormonal effect Effects 0.000 description 1
- GPRLSGONYQIRFK-UHFFFAOYSA-N hydron Chemical compound [H+] GPRLSGONYQIRFK-UHFFFAOYSA-N 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 235000014655 lactic acid Nutrition 0.000 description 1
- 239000004310 lactic acid Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 235000016709 nutrition Nutrition 0.000 description 1
- 230000035764 nutrition Effects 0.000 description 1
- 238000009329 organic farming Methods 0.000 description 1
- 239000011368 organic material Substances 0.000 description 1
- 230000036961 partial effect Effects 0.000 description 1
- 239000000575 pesticide Substances 0.000 description 1
- 238000002205 phenol-chloroform extraction Methods 0.000 description 1
- 150000003109 potassium Chemical class 0.000 description 1
- CHWRSCGUEQEHOH-UHFFFAOYSA-N potassium oxide Chemical compound [O-2].[K+].[K+] CHWRSCGUEQEHOH-UHFFFAOYSA-N 0.000 description 1
- 229910001950 potassium oxide Inorganic materials 0.000 description 1
- XXQBEVHPUKOQEO-UHFFFAOYSA-N potassium peroxide Inorganic materials [K+].[K+].[O-][O-] XXQBEVHPUKOQEO-UHFFFAOYSA-N 0.000 description 1
- CLSKHAYBTFRDOV-UHFFFAOYSA-N potassium;molecular oxygen Chemical compound [K+].O=O CLSKHAYBTFRDOV-UHFFFAOYSA-N 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 238000011002 quantification Methods 0.000 description 1
- 238000006722 reduction reaction Methods 0.000 description 1
- 230000010076 replication Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 230000002441 reversible effect Effects 0.000 description 1
- 235000009566 rice Nutrition 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- SUKJFIGYRHOWBL-UHFFFAOYSA-N sodium hypochlorite Chemical compound [Na+].Cl[O-] SUKJFIGYRHOWBL-UHFFFAOYSA-N 0.000 description 1
- 238000009987 spinning Methods 0.000 description 1
- 239000003381 stabilizer Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- FDDDEECHVMSUSB-UHFFFAOYSA-N sulfanilamide Chemical compound NC1=CC=C(S(N)(=O)=O)C=C1 FDDDEECHVMSUSB-UHFFFAOYSA-N 0.000 description 1
- 229950000244 sulfanilic acid Drugs 0.000 description 1
- 229940124530 sulfonamide Drugs 0.000 description 1
- 230000008685 targeting Effects 0.000 description 1
- 239000002562 thickening agent Substances 0.000 description 1
- 229940113082 thymine Drugs 0.000 description 1
- LENZDBCJOHFCAS-UHFFFAOYSA-N tris Chemical compound OCC(N)(CO)CO LENZDBCJOHFCAS-UHFFFAOYSA-N 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
- 238000012795 verification Methods 0.000 description 1
Landscapes
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
Description
本発明は、家畜糞尿を原料とする植物生長促進剤及び植物生長促進剤の製造方法に関する。 The present invention relates to a plant growth promoter and a method for producing a plant growth promoter using livestock manure as a raw material.
家畜糞尿を原料とする堆肥は、地力を維持し且つ作物の生産性を向上させる有機質資材である。化学肥料の普及後は、作物の生産性向上には化学肥料が多用されてきた。しかしながら、近年の減農薬農法、減化学肥料農法又は有機農法の広がりにともない、堆肥の使用量も再び増加している。 Compost made from livestock manure is an organic material that maintains soil fertility and improves crop productivity. After the spread of chemical fertilizers, chemical fertilizers have been widely used to improve crop productivity. However, with the recent spread of pesticide-reduced farming methods, reduced chemical fertilizer farming methods, or organic farming methods, the amount of compost used has increased again.
牛糞、豚糞、鶏糞等の家畜糞を堆肥化する方法が広く知られている(例えば、特許文献1)。特許文献1の堆肥製造方法では、鶏糞に木片チップと微生物を混入した60℃以上の混合物を、堆肥舎で6.5日間、その後発酵槽で23.5日間発酵させる。得られた発酵物から、選別機で木片チップを回収した後、鶏糞堆肥を養生施設に送り、切返しをしながら60℃以上で3.8日間発酵させて、鶏糞堆肥が完成する。 A method of composting livestock manure such as cow manure, pig manure, and chicken manure is widely known (for example, Patent Document 1). In the compost production method of Patent Document 1, a mixture of chicken manure mixed with wood chips and microorganisms at 60 ° C. or higher is fermented in a compost house for 6.5 days and then in a fermenter for 23.5 days. After collecting wood chips from the obtained fermented product with a sorter, the chicken manure compost is sent to a curing facility and fermented at 60 ° C. or higher for 3.8 days while turning back to complete the chicken manure compost.
このような堆肥を製造する際、堆肥の含水率を低くするため、***物から液体成分と固定成分とを分離することがある。この際に分離された液体成分についてはあまり利用されていなかった。 When producing such compost, the liquid component and the fixed component may be separated from the excrement in order to reduce the water content of the compost. The liquid component separated at this time was not used much.
そこで、本発明はこれらの点に鑑みてなされたものであり、家畜糞尿の液体成分を用いて植物の生長を促進することができる植物生長促進剤及び植物生長促進剤の製造方法を提供することを目的とする。 Therefore, the present invention has been made in view of these points, and provides a plant growth promoter and a method for producing a plant growth promoter capable of promoting plant growth using a liquid component of livestock manure. With the goal.
本発明は、以下の[1]〜[9]である。
[1]家畜の糞尿を原料とする植物生長促進剤であって、バクテロイデス門に含まれる微生物、クロロフレクサス門に含まれる微生物、ゲンマティモナス門に含まれる微生物、及びウェルコミクロビウム門に含まれる微生物からなる群のうち少なくともいずれか1つ以上を含む、植物生長促進剤。
[2]5′-CCTACGGGNGGCWGCAG-3′(配列番号1)で示される塩基配列(該塩基配列中、NはA、T、G又はCであり、WはA又はTである)を含む第1プライマーと5′-GACTACHVGGGTATCTAATCC-3′(配列番号2)で示される塩基配列(該塩基配列中、HはA、T又はCであり、VはA、C又はGである)を含む第2プライマーとを用いて、該植物生長促進剤中に含まれる微生物を検出したときに、バクテロイデス門に含まれる微生物、クロロフレクサス門に含まれる微生物、ゲンマティモナス門に含まれる微生物、及び、ウェルコミクロビウム門に含まれる微生物からなる群のうち少なくともいずれか1つ以上が検出される、[1]の植物生長促進剤。
[3]全炭素濃度が2,000mg/kg以下である、[1]又は[2]の植物生長促進剤。
[4]ケルダール法で測定した全窒素濃度が500mg/kg以下である、[1]〜[3]のいずれかの植物生長促進剤。
[5]全リン濃度が2,000mg/kg以下である、[1]〜[4]のいずれかの植物生長促進剤。
[6]全カリウム濃度が5,000mg/kg以下である、[1]〜[5]のいずれかの植物生長促進剤。
[7]前記植物生長促進剤は、液体、固形又はスラリーの態様である、[1]〜[6]のいずれかの植物生長促進剤。
[8]家畜の糞尿の液体成分を分離するステップと、5′-CCTACGGGNGGCWGCAG-3′(配列番号1)の塩基配列を含む第1プライマーと5′-GACTACHVGGGTATCTAATCC-3′(配列番号2)の塩基配列を含む第2プライマーとを用いて検出される微生物のうち、バクテロイデス門に含まれる微生物を1.5%以上、クロロフレクサス門に含まれる微生物を1.5%以上、ゲンマティモナス門に含まれる微生物を0.5%以上、及び、ウェルコミクロビウム門に含まれる微生物からなる群のうち少なくとも1種以上を0.5%以上含むようになるまで、前記液体成分を曝気させるステップとを含む、植物生長促進剤の製造方法。
[9] 前記曝気させるステップにおいて、F[m/s]を空気流量、V[m3]を処理液体積、HL[m]を処理液深度とした場合に、
を満たす状態において前記液体成分を曝気させる、[8]の植物生長促進剤の製造方法。
The present invention is the following [1] to [9].
[1] A plant growth promoter made from livestock manure, which is contained in microorganisms contained in the phylum Bacteroidetes, microorganisms contained in the phylum Chloroflexi, microorganisms contained in the phylum Gemmatimonadetes, and phylum Verrucomicrobia. A plant growth promoter comprising at least one or more of the group consisting of microorganisms.
[2] A first containing the base sequence represented by 5'-CCTACGGGNGGCWGCAG-3'(SEQ ID NO: 1) (in the base sequence, N is A, T, G or C, and W is A or T). A second primer containing a primer and the base sequence shown by 5'-GACTACHVGGGTATCTAATCC-3'(SEQ ID NO: 2) (in the base sequence, H is A, T or C and V is A, C or G). When the microorganisms contained in the plant growth promoter were detected using, the microorganisms contained in the phylum Bacteroidetes, the microorganisms contained in the phylum Chloroflexi, the microorganisms contained in the phylum Gemmatimonadetes, and Verrucomicrobia. The plant growth promoter according to [1], wherein at least one or more of the group consisting of microorganisms contained in the phylum Verrucomicrobia is detected.
[3] The plant growth promoter according to [1] or [2], which has a total carbon concentration of 2,000 mg / kg or less.
[4] The plant growth promoter according to any one of [1] to [3], wherein the total nitrogen concentration measured by the Kjeldahl method is 500 mg / kg or less.
[5] The plant growth promoter according to any one of [1] to [4], which has a total phosphorus concentration of 2,000 mg / kg or less.
[6] The plant growth promoter according to any one of [1] to [5], which has a total potassium concentration of 5,000 mg / kg or less.
[7] The plant growth promoter according to any one of [1] to [6], wherein the plant growth promoter is a liquid, solid or slurry embodiment.
[8] The step of separating the liquid component of livestock manure, the first primer containing the base sequence of 5'-CCTACGGGNGGCWGCAG-3'(SEQ ID NO: 1), and the base of 5'-GACTACHVGGGTATCTAATCC-3'(SEQ ID NO: 2). Among the microorganisms detected using the second primer containing the sequence, 1.5% or more of the microorganisms contained in the phylum Bacteroidetes and 1.5% or more of the microorganisms contained in the phylum Chloroflexus are contained in the phylum Gemmatimonadetes. The step of aerating the liquid component until it contains 0.5% or more of the microorganisms and 0.5% or more of at least one of the group consisting of microorganisms contained in the Welcomicrobium phylum. A method for producing a plant growth promoter, including.
[9] In the aeration step, when F [m / s] is the air flow rate, V [m 3 ] is the treatment liquid volume, and HL [m] is the treatment liquid depth.
[8] The method for producing a plant growth promoter, which aerates the liquid component in a state satisfying the above conditions.
本発明の植物生長促進剤は、植物の生長を促進することができるという効果を奏する。そして、この植物の生長促進効果は、一般的に肥料に含まれるリンや窒素分の量が少なくても発揮される。 The plant growth promoter of the present invention has the effect of promoting the growth of plants. The growth promoting effect of this plant is generally exhibited even if the amount of phosphorus and nitrogen contained in the fertilizer is small.
[植物生長促進剤の成分]
本発明者らは、鋭意研究の結果、本実施の形態に係る家畜の糞尿の液体成分を原料とする植物生長促進剤が特定の微生物群を含むことにより、安定的な植物生長効果をもたらすことを見出した。家畜は、例えば、牛、豚、鶏、羊又は山羊であるが、これらの動物に限定されない。
[Ingredients of plant growth promoter]
As a result of diligent research, the present inventors have determined that the plant growth promoter using the liquid component of livestock manure according to the present embodiment contains a specific microbial group to bring about a stable plant growth effect. I found. Livestock are, for example, cows, pigs, chickens, sheep or goats, but are not limited to these animals.
本発明の植物生長促進剤は、バクテロイデス門に含まれる微生物、クロロフレクサス門に含まれる微生物、ゲンマティモナス門に含まれる微生物、及びウェルコミクロビウム門に含まれる微生物からなる群のうち少なくともいずれか1つ以上の微生物を含む。 The plant growth promoter of the present invention is at least one of a group consisting of microorganisms contained in the phylum Bacteroidetes, microorganisms contained in the phylum Chloroflexi, microorganisms contained in the phylum Gemmatimonadetes, and microorganisms contained in the phylum Verrucomicrobia. Contains one or more microorganisms.
[バクテロイデス門]
バクテロイデス門は、グラム陰性細菌のグループであり、腸内細菌として知られている微生物が含まれる。下位分類(綱)として、バクテロイデス綱、フラボバクテリア綱、スフィンゴバクテリア綱、キティノファガ綱、キトファガ綱、サプロスピラ綱を含む。バクテロイデス門に含まれる微生物としては、例えば、Bacteroides plebeius、Bacteroides fragilisが挙げられる。
本発明の植物生長促進剤中、バクテロイデス門の微生物の含有割合は、好ましくは1.5%以上(後述する方法により本発明の植物生長促進剤から検出される微生物全体に対する割合。以下、微生物の含有割合については同様である。)であり、より好ましくは、5〜12%である。
[Bacteroides Gate]
The phylum Bacteroides is a group of Gram-negative bacteria that include microorganisms known as gut flora. Subclasses (Classes) include Bacteroidia, Flavobacteriia, Sphingobacteriia, Kitinofaga, Chitofaga, and Saprospira. Examples of microorganisms contained in the phylum Bacteroides include Bacteroides plebeius and Bacteroides fragilis.
The content ratio of the microorganisms of the phylum Bacteroides in the plant growth promoter of the present invention is preferably 1.5% or more (the ratio of the microorganisms to the total microorganisms detected from the plant growth promoter of the present invention by the method described later. The content ratio is the same.), More preferably 5 to 12%.
[クロロフレクサス門]
クロロフレクサス門は、緑色滑走細菌門とも呼ばれ、下位分類(綱)として、クロロフレクサス綱、アナエロリネア綱、アルデンティカテナ綱、カルディリネア綱、クテドノバクテル綱、テルモフレクスス綱、テルモミクロビウム綱を含む。クロロフレクサス門に含まれる微生物としては、例えば、Thermomicrobium roseum、Sphaerobacter thermophilus、Caldilinea aerophila、Caldilinea tarbellica、Ktedonobacter、Thermosporothrix、Thermogemmatispora onikobensis、Thermogemmatispora foliorumが挙げられる。
本発明の植物生長促進剤中、クロロフレクサス門の微生物の含有割合は、好ましくは1.5%以上であり、より好ましくは、2〜15%である。
[Chloroflexi Gate]
The phylum Chloroflexi, also called the phylum Chloroflexi, includes the subclasses (Classes) Chloroflexi, Anaerolinea, Ardenticatena, Cardilinea, Cutedonovactel, Thermoflexus, and Thermomicrobium. Examples of microorganisms contained in the phylum Chloroflexi include Thermomicrobium roseum, Sphaerobacter thermophilus, Caldilinea aerophila, Caldilinea tarbellica, Ktedonobacter, Thermosporothrix, Thermogemmatispora onikobensis, and Thermogemmatispora foliorum.
In the plant growth promoter of the present invention, the content ratio of microorganisms of the phylum Chloroflexi is preferably 1.5% or more, more preferably 2 to 15%.
[ゲンマティモナス門]
ゲンマティモナス門は、グラム陰性細菌の門である。下位分類(綱)として、ゲンマティモナス綱、ロンギミクロビウム綱が含まれる。ゲンマティモナス門に含まれる微生物としては、例えば、Gemmatimonas aurantiaca、Gemmatimonas phototrophica、Longimicrobium terrae、Gemmatirosa kalamazoonesisが挙げられる。
本発明の植物生長促進剤中、ゲンマティモナス門の微生物の含有割合は、好ましくは1.5%以上であり、より好ましくは、2%〜5%である。
[Gemmatimonadetes]
The phylum Gemmatimonadetes is the phylum of Gram-negative bacteria. Subclasses (Classes) include Gemmatimonadetes and Longimicrobium. Examples of microorganisms contained in the phylum Gemmatimonas include Gemmatimonas aurantiaca, Gemmatimonas phototrophica, Longimicrobium terrae, and Gemmatirosa kalamazoonesis.
In the plant growth promoter of the present invention, the content ratio of the microorganism of Gemmatimonadetes is preferably 1.5% or more, more preferably 2% to 5%.
[ウェルコミクロビウム門]
ウェルコミクロビウム門は、グラム陰性細菌の門である。下位分類(綱)として、ウェルコミクロビウム綱、オピトゥトゥス綱を含む。ウェルコミクロビウム門に含まれる微生物としては、例えば、Verrucomicrobium Haloferula、Verrucomicrobium Luteolibacter、 Verrucomicrobium Persicirhabdus、Verrucomicrobium Prosthecobacter、Verrucomicrobium Roseibacillus、Verrucomicrobium Roseimicrobium、Prosthecobacter dejongeii、Chthoniobacter flavus、Ellin514株、Puniceicoccus Cerasicoccusが挙げられる。
本発明の植物生長促進剤中、ウェルコミクロビウム門の微生物の含有割合は、好ましくは1.5%以上であり、より好ましくは、2%〜5%である。
[Verrucomicrobia]
The phylum Verrucomicrobia is the phylum of Gram-negative bacteria. Subclasses (classes) include Verrucomicrobiae and Opitutus. Examples of microorganisms contained in the phylum Verrucomicrobia include Verrucomicrobium Haloferula, Verrucomicrobium Luteolibacter, Verrucomicrobium Persicirhabdus, Verrucomicrobium Prosthecobacter, Verrucomicrobium Roseibacillus, Verrucomicrobium Roseimicrobium, Prosthecobacter dejonge.
In the plant growth promoter of the present invention, the content ratio of the microorganism of the phylum Verrucomicrobia is preferably 1.5% or more, more preferably 2% to 5%.
本発明の植物生長促進剤がこのような微生物を含むことにより、植物生長促進剤に含有されていた有機物が消費されていることに加えて、植物生長促進剤の原料である家畜の糞尿の液体成分に元々含まれていた植物発芽阻害物質が微生物により分解されていると推測される。その結果、本発明の植物生長促進剤は、安定した植物生長効果をもたらすことができると考えられる。 Since the plant growth promoter of the present invention contains such microorganisms, the organic matter contained in the plant growth promoter is consumed, and in addition, the liquid of livestock manure which is the raw material of the plant growth promoter It is presumed that the plant germination inhibitor originally contained in the components is decomposed by microorganisms. As a result, it is considered that the plant growth promoter of the present invention can bring about a stable plant growth effect.
本発明の植物生長促進剤は、さらに、アシドバクテリア門に含まれる微生物、クロロビウム門に属する微生物、及びプロテオバクテリア門に属する微生物からなる群から選ばれる一種以上の微生物を1.5%以上含むことが好ましい。 The plant growth promoter of the present invention further contains 1.5% or more of one or more microorganisms selected from the group consisting of microorganisms belonging to the phylum Acidobacteria, microorganisms belonging to the phylum Chlorobia, and microorganisms belonging to the phylum Proteobacteria. Is preferable.
[リアルタイムPCRとシーケンスによる微生物の検出]
植物生長促進剤中において16S rRNAをターゲットとする第1プライマー及び第2プライマーを用いたリアルタイムPCRを行うことにより植物生長促進剤に含まれる微生物群を特定することができる。リアルタイムPCRでは、PCR増幅産物の増加をリアルタイムに解析することにより、鋳型DNAを定量する。16S rRNAは、どの微生物においても配列の相動性が高いことから微生物の定量の指標として用いることができる。
[Detection of microorganisms by real-time PCR and sequencing]
The group of microorganisms contained in the plant growth promoter can be identified by performing real-time PCR using the first primer and the second primer targeting 16S rRNA in the plant growth promoter. In real-time PCR, template DNA is quantified by analyzing the increase in PCR amplification products in real time. 16S rRNA can be used as an index for quantification of microorganisms because the sequence compatibility is high in any microorganism.
第1プライマー及び第2プライマーは、リアルタイムPCRにおいてDNAポリメラーゼによる鋳型DNAの複製の開始起点となるオリゴヌクレオチドである。第1プライマーとして、配列番号1:
5′-CCTACGGGNGGCWGCAG-3′(配列番号1)
で示される塩基配列を含むDNA分子を用い、第2プライマーとして、配列番号2:
5′-GACTACHVGGGTATCTAATCC-3′(配列番号2)
で示される塩基配列を含むDNA分子を用いることができる。
The first and second primers are oligonucleotides that serve as the starting point for replication of the template DNA by DNA polymerase in real-time PCR. As the first primer, SEQ ID NO: 1:
5'-CCTACGGGNGGCWGCAG-3' (SEQ ID NO: 1)
Using a DNA molecule containing the base sequence shown by, as a second primer, SEQ ID NO: 2:
5'-GACTACHVGGGTATCTAATCC-3' (SEQ ID NO: 2)
A DNA molecule containing the base sequence shown by can be used.
配列番号1で示される塩基配列中、NはA(アデニン)、T(チミン)、G(グアニン)又はC(シトシン)であり、WはA又はTである。配列番号2で示される塩基配列中、HはA、T又はCであり、VはA、C又はGである。 In the nucleotide sequence shown in SEQ ID NO: 1, N is A (adenine), T (thymine), G (guanine) or C (cytosine), and W is A or T. In the base sequence shown in SEQ ID NO: 2, H is A, T or C, and V is A, C or G.
第1プライマーは、配列番号1で示される塩基配列の5’側又は3’側に追加的な塩基配列を含んでもよい。このようなプライマーの例としては、5’側に追加的な塩基配列を含む配列番号3:
5′-TCGTCGGCAGCGTCAGATGTGTATAAGAGACAGCCTACGGGNGGCWGCAG-3′のDNA分子が挙げられる。同様に、第2プライマーは、配列番号2で示される塩基配列の5’側又は3’側に追加的な塩基配列を含んでもよい。このようなプライマーの例としては、5’側に追加的な塩基配列を含む配列番号4:
5′-GTCTCGTGGGCTCGGAGATGTGTATAAGAGACAGGACTACHVGGGTATCTAATCC-3′のDNA分子が挙げられる。
The first primer may contain an additional base sequence on the 5'side or 3'side of the base sequence shown in SEQ ID NO: 1. An example of such a primer is SEQ ID NO: 3: which contains an additional base sequence on the 5'side.
The DNA molecule of 5'-TCGTCGGCAGCGTCAGATGTGTATAAGAGACAGCCTACGGGNGGCWGCAG-3' can be mentioned. Similarly, the second primer may contain an additional base sequence on the 5'side or 3'side of the base sequence shown in SEQ ID NO: 2. An example of such a primer is SEQ ID NO: 4: which contains an additional base sequence on the 5'side.
The DNA molecule of 5'-GTCTCGTGGGCTCGGAGATGTGTATAAGAGACAGGACTACHVGGGTATCTAATCC-3' can be mentioned.
リアルタイムPCRにより増幅されたDNA分子の配列を解読することにより、微生物群の種をそれぞれ特定することができる。解読されたDNA配列と既知の種のDNA配列との相同性が97%以上である場合に、解読されたDNA配列がこの既知の種由来の16S rRNAの鋳型DNA配列又は鋳型DNAの相補鎖のDNA配列であると判定することができる。 By sequencing the DNA molecules amplified by real-time PCR, the species of each microbial community can be identified. When the homology between the decoded DNA sequence and the DNA sequence of a known species is 97% or more, the decoded DNA sequence is the template DNA sequence of 16S rRNA derived from this known species or the complementary strand of the template DNA. It can be determined that it is a DNA sequence.
図1は、本発明の植物生長促進剤の一例(以下「植物生長促進剤A」という。)中の微生物をリアルタイムPCRで定量した際の解析結果を示す。図1には、リアルタイムPCRにより検出された代表的な微生物のリード数を門ごとに示す。リード数は、リアルタイムPCRにより増幅されたDNA分子の塩基配列を解読した結果、図1に示す門に属する微生物由来であると判定されたDNA分子の数である。図1の全リード数に対する割合は、塩基配列を解読したDNA分子の総数(全リード数)に対するリード数の割合の百分率である。なお、図1に示す結果を得るための解析方法の詳細については後述する。 FIG. 1 shows the analysis results when the microorganisms in an example of the plant growth promoter of the present invention (hereinafter referred to as “plant growth promoter A”) were quantified by real-time PCR. FIG. 1 shows the number of reads of typical microorganisms detected by real-time PCR for each phyla. The number of reads is the number of DNA molecules determined to be derived from the microorganism belonging to the phylum shown in FIG. 1 as a result of decoding the base sequence of the DNA molecule amplified by real-time PCR. The ratio to the total number of reads in FIG. 1 is a percentage of the ratio of the number of reads to the total number of DNA molecules whose nucleotide sequences have been decoded (total number of reads). The details of the analysis method for obtaining the result shown in FIG. 1 will be described later.
植物生長促進剤AのリアルタイムPCRによる解析結果では、図1に示すように、全リード数に対するそれぞれの門に属する微生物のリード数の割合は、アシドバクテリア門に含まれる微生物が14.88%、バクテロイデス門に含まれる微生物が6.804%、クロロビウム門に含まれる微生物が8.619%、クロロフレクサス門に含まれる微生物が8.952%、ゲンマティモナス門に含まれる微生物が3.12%、未培養門OD1に含まれる微生物が2.929%、プロテオバクテリア門に含まれる微生物が36.792%、ウェルコミクロビウム門に含まれる微生物が2.83%であった。 According to the results of real-time PCR analysis of the plant growth promoter A, as shown in FIG. 1, the ratio of the number of leads of microorganisms belonging to each phylum to the total number of reads was 14.88% for the microorganisms contained in the phylum Acidobacteria. 6.804% of the microorganisms contained in the phylum Bacteroides, 8.619% of the microorganisms contained in the phylum Chlorobium, 8.952% of the microorganisms contained in the phylum Chlorofexus, and 3.12% of the microorganisms contained in the phylum Genmatimonas. , 2.929% of the microorganisms contained in the uncultured phylum OD1, 36.792% of the microorganisms contained in the Proteobacterium phylum, and 2.83% of the microorganisms contained in the Welcomicrobium phylum.
植物生長促進剤Aに含まれる微生物の割合は、植物生長促進剤Aの製造場所の地理的条件等により多少ばらつくことがあるが、図1に示す下限値は、このばらつきによらずに検出可能な微生物の割合の下限値である。この下限値は、図1に示す全リード数に対する割合と同様に、それぞれの門に含まれる微生物が植物生長促進剤AのリアルタイムPCRにおいて検出されるリード数の全リード数に対する百分率を示す。図1の下限値の欄に示すように、植物生長促進剤Aは、アシドバクテリア門に含まれる微生物を3.5%以上、バクテロイデス門に含まれる微生物を1.5%以上、クロロビウム門に含まれる微生物を1.5%以上、クロロフレクサス門に含まれる微生物を1.5%以上、ゲンマティモナス門に含まれる微生物を0.5%以上、未培養門OD1に含まれる微生物を0.5%以上、プロテオバクテリア門に含まれる微生物を8%以上、ウェルコミクロビウム門に含まれる微生物を0.5%以上少なくとも含む。 The proportion of microorganisms contained in the plant growth promoter A may vary slightly depending on the geographical conditions of the place where the plant growth promoter A is produced, but the lower limit shown in FIG. 1 can be detected regardless of this variation. It is the lower limit of the proportion of various microorganisms. This lower limit indicates the percentage of the total number of reads that the microorganisms contained in each phylum are detected in the real-time PCR of the plant growth promoter A, similar to the ratio to the total number of reads shown in FIG. As shown in the lower limit column of FIG. 1, the plant growth promoter A contains 3.5% or more of microorganisms contained in the phylum Acidobacteria, 1.5% or more of microorganisms contained in the phylum Bacteroidetes, and phylum Chlorobium. 1.5% or more of the microorganisms contained in the phylum Chloroflexus, 1.5% or more of the microorganisms contained in the phylum Proteobacteria, 0.5% or more of the microorganisms contained in the uncultivated phylum OD1 % Or more, 8% or more of microorganisms contained in the phylum Proteobacteria, and 0.5% or more of microorganisms contained in the phylum Welcomicrobium.
[炭素分]
本発明の植物生長促進剤は、家畜の糞尿由来であり、炭素分(有機物)を含有していてもよい。ただし、本発明の植物生長促進剤は、炭素分が少ない方が好ましく、好ましくは、全炭素濃度が2,000mg/kg以下である。このように、植物生長促進剤における炭素の濃度が、原料の糞尿に含有される炭素の濃度よりも低いので、植物に植物生長促進剤を与えた場合に、土壌中の有機物の濃度が高くなることを抑制することができる。このため、本発明の植物生長促進剤は、土壌中の酸素の欠乏や植物の根腐れを引き起こすことを抑制することができる。
[Carbon]
The plant growth promoter of the present invention is derived from livestock manure and may contain carbon (organic matter). However, the plant growth promoter of the present invention preferably has a low carbon content, and preferably has a total carbon concentration of 2,000 mg / kg or less. In this way, the concentration of carbon in the plant growth promoter is lower than the concentration of carbon contained in the manure of the raw material, so that when the plant is given the plant growth promoter, the concentration of organic matter in the soil becomes high. Can be suppressed. Therefore, the plant growth promoter of the present invention can suppress the cause of oxygen deficiency in soil and root rot of plants.
本発明の植物生長促進剤は、窒素分を含有していてもよいが、窒素分が少なくとも植物生長促進効果を発揮することができる。本発明の植物生長促進剤は、好ましくは、全窒素濃度が500mg/kg以下である。この全窒素濃度は、一般的な肥料に含まれる全窒素濃度と比較すると少ない。 The plant growth-promoting agent of the present invention may contain nitrogen, but the nitrogen content can at least exert a plant growth-promoting effect. The plant growth promoter of the present invention preferably has a total nitrogen concentration of 500 mg / kg or less. This total nitrogen concentration is lower than the total nitrogen concentration contained in general fertilizers.
本発明の植物生長促進剤は、リン分を含有していてもよいが、リン分が少なくとも植物生長促進効果を発揮することができる。本発明の植物生長促進剤は、好ましくは、全リン濃度が2,000mg/kg以下である。この全リン濃度は、一般的な肥料に含まれる全リン濃度と比較すると少ない。 The plant growth promoter of the present invention may contain phosphorus, but the phosphorus can at least exert a plant growth promoting effect. The plant growth promoter of the present invention preferably has a total phosphorus concentration of 2,000 mg / kg or less. This total phosphorus concentration is lower than the total phosphorus concentration contained in general fertilizers.
本発明の植物生長促進剤は、カリウム(塩であってもよい)を含有していてもよいが、カリウムが少なくとも植物生長促進効果を発揮することができる。本発明の植物生長促進剤は、好ましくは、カリウム濃度が5,000mg/kg以下である。このカリウム濃度は、一般的な肥料に含まれる全リン濃度と比較すると少ない。 The plant growth-promoting agent of the present invention may contain potassium (which may be a salt), but potassium can at least exert a plant growth-promoting effect. The plant growth promoter of the present invention preferably has a potassium concentration of 5,000 mg / kg or less. This potassium concentration is low compared to the total phosphorus concentration contained in general fertilizers.
本発明の植物生長促進剤は、剤型は限定されず、液体、固形又はスラリー等のいずれであってもよいが、液体であることが好ましい。
また、本発明の植物生長促進剤は、剤型に応じた副成分、例えば、希釈剤、安定剤、増粘剤、造粒剤などを含んでいてもよい。
The dosage form of the plant growth promoter of the present invention is not limited and may be liquid, solid, slurry or the like, but it is preferably liquid.
In addition, the plant growth promoter of the present invention may contain auxiliary components according to the dosage form, for example, a diluent, a stabilizer, a thickener, a granulator and the like.
本発明の植物生長促進剤の好適な態様として、全窒素濃度が500mg/kg以下であり、全リン濃度が2,000mg/kg以下であり、全カリウム濃度が5,000mg/kg以下であり、アンモニア性窒素の濃度が200mg/L以下であり、水溶性リン酸の五酸化リン酸換算の濃度が5質量%以下であり、且つ、水溶性カリウムの二酸化カリウム換算の濃度が5質量%以下である植物生長促進剤が挙げられる。本発明の植物生長促進剤における窒素、リン及び水溶性カリウムの濃度は、一般的な肥料における窒素、リン及び水溶性カリウムの濃度より低い。本発明の植物生長促進剤は、窒素等の濃度が低いにもかかわらず、後述の実施例において確認されているように植物生長促進効果がある。このことから、植物生長促進剤には上記微生物に起因する植物ホルモン様物質が含まれていると推定される。 As a preferred embodiment of the plant growth promoter of the present invention, the total nitrogen concentration is 500 mg / kg or less, the total phosphorus concentration is 2,000 mg / kg or less, and the total potassium concentration is 5,000 mg / kg or less. When the concentration of ammoniacal nitrogen is 200 mg / L or less, the concentration of water-soluble phosphoric acid in terms of phosphoric acid pentoxide is 5% by mass or less, and the concentration of water-soluble potassium in terms of potassium dioxide is 5% by mass or less. Some plant growth promoters are mentioned. The concentration of nitrogen, phosphorus and water-soluble potassium in the plant growth promoter of the present invention is lower than the concentration of nitrogen, phosphorus and water-soluble potassium in general fertilizers. Although the plant growth promoter of the present invention has a low concentration of nitrogen and the like, it has a plant growth promoting effect as confirmed in Examples described later. From this, it is presumed that the plant growth promoter contains a plant hormone-like substance caused by the above-mentioned microorganism.
[植物生長促進剤の好適な製造方法の例]
本発明の植物生長促進剤は、例えば、家畜、好ましくは牛や豚の糞尿を数日間以上曝気させることにより得ることができる。糞尿を曝気させることにより、上記した微生物が増殖し、本発明の植物生長促進剤が得られる。
曝気させる期間は、好ましくは、1ヶ月以上であり、より好ましくは、10ヶ月以上であり、さらに好ましくは12ヶ月以上であり、特に好ましくは、13ヶ月〜18ヶ月である。
[Example of suitable production method of plant growth promoter]
The plant growth promoter of the present invention can be obtained, for example, by aerating livestock, preferably cow or pig manure, for several days or longer. By aeration of manure, the above-mentioned microorganisms proliferate, and the plant growth promoter of the present invention is obtained.
The period of aeration is preferably 1 month or longer, more preferably 10 months or longer, still more preferably 12 months or longer, and particularly preferably 13 to 18 months.
[植物生長促進剤の好適な製造方法]
本発明の植物生長促進剤の好適な製造方法を説明する。本発明の植物生長促進剤は、好ましくは、以下の(1)及び(2)のステップを含む方法により製造される。
(1)家畜の糞尿の液体成分を分離するステップ
(2)液体成分を曝気させるステップ
(1)のステップでは、家畜の糞尿を蓄積し、蓄積した糞尿の液体成分を分離する。例えば、家畜の糞尿の上澄み液を液体成分として分離する。
[Preferable manufacturing method of plant growth promoter]
A suitable method for producing the plant growth promoter of the present invention will be described. The plant growth promoter of the present invention is preferably produced by a method including the following steps (1) and (2).
(1) Step of separating the liquid component of livestock manure (2) Step of aerating the liquid component In the step of (1), livestock manure is accumulated and the accumulated liquid component of manure is separated. For example, the supernatant of livestock manure is separated as a liquid component.
(2)のステップでは、家畜の糞尿の液体成分を曝気処理槽において曝気する。曝気処理槽においては、糞尿の液体成分中へ空気を送り込み、送り込んだ空気に液体を触れさせることにより、糞尿の液体成分を曝気させることができる。曝気処理槽のサイズに特に制限は設けないが、例えば、1L〜100kLの間である。曝気処理槽のサイズは、望ましくは10L〜10kL、更に望ましくは500L〜5kLである。処理液の供給形態は制限されるものではないが、曝気処理槽に連続的又は半連続的に家畜の糞尿又はその液体成分が供給されることが望ましい。 In step (2), the liquid component of livestock manure is aerated in an aeration treatment tank. In the aeration treatment tank, the liquid component of manure can be aerated by sending air into the liquid component of manure and bringing the liquid into contact with the sent air. The size of the aeration treatment tank is not particularly limited, but is, for example, between 1 L and 100 kL. The size of the aeration treatment tank is preferably 10 L to 10 kL, more preferably 500 L to 5 kL. The form of supply of the treatment liquid is not limited, but it is desirable that livestock manure or a liquid component thereof is continuously or semi-continuously supplied to the aeration treatment tank.
図2は、植物生長促進剤Aを製造するための製造装置100の一例を示す。製造装置100は、糞尿貯め10と、供給部20と、第1曝気処理槽30a〜第4曝気処理槽30dと、コンプレッサ40a〜コンプレッサ40dと、回収部50とを備える。糞尿貯め10は、牛舎中の牛の糞尿を貯える。供給部20は、糞尿貯め10と第1曝気処理槽30aとの間に接続されたパイプを介して、糞尿貯め10に貯えられた糞尿をポンプにより第1曝気処理槽30aへ供給する。供給部20は、自動的且つ断続的に糞尿を供給し、例えば、1ヵ月に1回のペースで糞尿を供給する。 FIG. 2 shows an example of a manufacturing apparatus 100 for manufacturing a plant growth promoter A. The manufacturing apparatus 100 includes a manure storage 10, a supply unit 20, a first aeration treatment tank 30a to a fourth aeration treatment tank 30d, a compressor 40a to a compressor 40d, and a recovery unit 50. The manure reservoir 10 stores manure from cows in the barn. The supply unit 20 pumps the manure stored in the manure storage 10 to the first aeration treatment tank 30a via a pipe connected between the manure storage 10 and the first aeration treatment tank 30a. The supply unit 20 automatically and intermittently supplies manure, for example, manure once a month.
第1曝気処理槽30a〜第4曝気処理槽30dは、槽内に貯えている家畜の糞尿の液体成分を曝気させる。図2は、製造装置100が4つの槽を有する例を示すが、製造装置100は1槽のみを有してもよく、直列に配置された2〜8槽を有してもよい。第1曝気処理槽30aのサイズは、一例としては縦3m、横3m、深さ2.5mであり、第2曝気処理槽30b〜第4曝気処理槽30dは、第1曝気処理槽30aと同じサイズであってもよい。 The first aeration treatment tanks 30a to the fourth aeration treatment tanks 30d aerate the liquid components of livestock manure stored in the tanks. FIG. 2 shows an example in which the manufacturing apparatus 100 has four tanks, but the manufacturing apparatus 100 may have only one tank, or may have 2 to 8 tanks arranged in series. The size of the first aeration treatment tank 30a is, for example, 3 m in length, 3 m in width, and 2.5 m in depth, and the second aeration treatment tank 30b to the fourth aeration treatment tank 30d are the same as the first aeration treatment tank 30a. It may be the size.
第1曝気処理槽30a〜第4曝気処理槽30dは、糞尿を固体成分と液体成分とに分離する。第1曝気処理槽30a〜第4曝気処理槽30dは、槽内の糞尿の固体成分を沈降させる。一方、第1曝気処理槽30aからあふれた糞尿の液体成分は、第2曝気処理槽30bへ移動する。液体成分が、第3曝気処理槽30c、第4曝気処理槽30dへ順次移動し、それぞれの曝気処理層において糞尿の固体成分が沈降することにより、糞尿の固体成分がほぼ除去される。 The first aeration treatment tank 30a to the fourth aeration treatment tank 30d separate manure into a solid component and a liquid component. The first aeration treatment tank 30a to the fourth aeration treatment tank 30d settle the solid component of manure in the tank. On the other hand, the liquid component of manure overflowing from the first aeration treatment tank 30a moves to the second aeration treatment tank 30b. The liquid component sequentially moves to the third aeration treatment tank 30c and the fourth aeration treatment tank 30d, and the solid component of manure is settled in each aeration treatment layer, so that the solid component of manure is substantially removed.
コンプレッサ40a〜コンプレッサ40dは、空気を圧縮して、第1曝気処理槽30a〜第4曝気処理槽30d内において糞尿の液体成分中に圧縮した空気を送り込むための装置である。第1曝気処理槽30a〜第4曝気処理槽30dでは、コンプレッサ40a〜コンプレッサ40dにより送り込まれた空気に液体成分が触れるので、液体成分を曝気させることができる。第1曝気処理槽30a〜第4曝気処理槽30dは、コンプレッサ40a〜コンプレッサ40dを用いて液体成分内の微生物の増殖に要する酸素を供給することにより、微生物の増殖を促進させることができる。微生物の増殖を促進させることで、糞尿の液体成分に含まれる植物発芽阻害成分の分解量を増やすことができる。 The compressors 40a to 40d are devices for compressing air and sending the compressed air into the liquid component of manure in the first aeration treatment tank 30a to the fourth aeration treatment tank 30d. In the first aeration treatment tanks 30a to the fourth aeration treatment tank 30d, since the liquid component comes into contact with the air sent by the compressors 40a to 40d, the liquid component can be aerated. The first aeration treatment tanks 30a to the fourth aeration treatment tanks 30d can promote the growth of microorganisms by supplying oxygen required for the growth of microorganisms in the liquid component by using the compressors 40a to 40d. By promoting the growth of microorganisms, the amount of decomposition of the plant germination inhibitor component contained in the liquid component of manure can be increased.
(2)のステップでは、F[m/s]を空気流量、V[m3]を処理液体積、HL[m]を処理液深度とした場合に、
曝気が行われている間の糞尿の液体成分の温度は、0℃〜40℃の範囲である。曝気が行われている間の糞尿の液体成分のpHは、6.0〜8.0の間が好適である。 The temperature of the liquid component of manure during aeration is in the range of 0 ° C to 40 ° C. The pH of the liquid component of manure during aeration is preferably between 6.0 and 8.0.
曝気時間は、糞尿の液体成分の植物発芽阻害成分が十分に除去できるまでの時間であり、好ましくは、1ヶ月以上、さらに好ましくは12カ月以上である。 The aeration time is the time until the plant germination inhibitory component of the liquid component of manure can be sufficiently removed, and is preferably 1 month or longer, more preferably 12 months or longer.
また、微生物による植物発芽阻害成分の除去を促進させるため、外部から何らかの従属栄養性好気微生物を添加してもよい。従属栄養性好気微生物は、例えば、酵母、乳酸菌等である。 Further, in order to promote the removal of the plant germination inhibitory component by the microorganism, some heterotrophic aerobic microorganism may be added from the outside. Heterotrophic aerobic microorganisms are, for example, yeast, lactic acid bacteria and the like.
図2の回収部50は、例えばポンプを用いて、第4曝気処理槽30dに接続されたパイプを介して、曝気された後の液体成分を植物生長促進剤として回収する。回収された植物生長促進剤では、(2)のステップの処理を実行することにより、含有する微生物が増殖しており、第1プライマー及び第2プライマーを用いて検出される微生物のうち、バクテロイデス門に含まれる微生物を1.5%以上、クロロフレクサス門に含まれる微生物を1.5%以上、ゲンマティモナス門に含まれる微生物を0.5%以上、又は、ウェルコミクロビウム門に含まれる微生物を0.5%以上含む。 The recovery unit 50 in FIG. 2 recovers the liquid component after aeration as a plant growth promoter through a pipe connected to the fourth aeration treatment tank 30d, for example, using a pump. In the recovered plant growth promoter, the microorganisms contained in the recovered plant growth promoter are grown by carrying out the treatment of step (2), and among the microorganisms detected using the first primer and the second primer, the phylum Bacteroidetes 1.5% or more of microorganisms contained in, 1.5% or more of microorganisms contained in Chloroflexi, 0.5% or more of microorganisms contained in Gemmatimonadetes, or Verrucomicrobia Contains 0.5% or more of microorganisms.
回収された植物生長促進剤は、そのままもしくは50倍まで希釈して植物に使用することができ、植物生長促進剤単体、又は植物生長促進剤と無機肥料もしくは有機肥料とを混合して使用することにより、相乗的に植物生長促進効果が期待できる。 The recovered plant growth promoter can be used as it is or diluted up to 50 times for plants, and the plant growth promoter alone or a mixture of the plant growth promoter and an inorganic fertilizer or an organic fertilizer should be used. Therefore, a synergistic effect of promoting plant growth can be expected.
回収された植物生長促進剤は、(2)のステップにおいて微生物により液体成分に含まれる有機物がほぼ完全に消費されているので、植物に植物生長促進剤を加えた場合に、土壌中の有機物濃度が高くなることを抑制することができる。このため、高い有機物濃度に起因する酸素の欠乏や植物の根腐れを抑制することができる。また、これまで利用方法が乏しかった家畜糞尿の液体成分を植物生長促進剤として有効活用することができる。植物生長促進剤を使用する対象となる植物の栽培形態は特に限定されず、畑作、稲作及び水耕栽培において生長促進効果を示すことが確認されている。また、植物生長促進剤に有機肥料又は無機肥料以外の副成分を混合した状態で植物の生長促進のために用いてもよい。 In the recovered plant growth promoter, the organic matter contained in the liquid component is almost completely consumed by the microorganisms in the step (2). Therefore, when the plant growth promoter is added to the plant, the concentration of the organic matter in the soil Can be suppressed from becoming high. Therefore, oxygen deficiency and root rot of plants due to high organic matter concentration can be suppressed. In addition, the liquid component of livestock manure, which has been poorly used so far, can be effectively used as a plant growth promoter. The cultivation form of the target plant to which the plant growth promoter is used is not particularly limited, and it has been confirmed that it exhibits a growth promoting effect in upland farming, rice cultivation and hydroponics. Further, it may be used for promoting the growth of plants in a state where the plant growth promoter is mixed with auxiliary components other than organic fertilizer or inorganic fertilizer.
[実施例1]
[植物生長促進剤Aの製造]
図2に示した製造装置100を用いて植物生長促進剤Aを製造した。植物生長促進剤Aの原材料として牛舎中の牛の糞尿を用いた。図2の第4曝気処理槽30dの貯留液から1ヶ月に1回約6トンの植物生長促進剤Aを取り出した。第1曝気処理槽30a〜第4曝気処理槽30dの体積はそれぞれ20kLとした。曝気量は各曝気処理槽で約3.75m3/分とした。F[m/s]を空気流量、V[m3]を処理液体積、HL[m]を処理液深度とした場合に、以下の式(a):
[Manufacturing of plant growth promoter A]
The plant growth promoter A was produced using the production apparatus 100 shown in FIG. Manure from cows in the barn was used as a raw material for the plant growth promoter A. Approximately 6 tons of plant growth promoter A was taken out from the reservoir of the fourth aeration treatment tank 30d in FIG. 2 once a month. The volumes of the first aeration treatment tank 30a to the fourth aeration treatment tank 30d were set to 20 kL, respectively. The amount of aeration was about 3.75 m 3 / min in each aeration treatment tank. When F [m / s] is the air flow rate, V [m 3 ] is the treatment liquid volume, and HL [m] is the treatment liquid depth, the following equation (a):
[植物生長促進剤Aの組成分析]
簡易CODメーターHC−607を用いて化学的酸素要求量(COD)を測定した。水素イオン濃度pHは、JIS K0102 17.1に従い、ガラス電極法を用いて測定した。全炭素濃度は、全有機炭素計(TOC−V,SSM−5000A,島津製作所)を用いて測定した。全窒素濃度の測定では、ケルダール法により変換されたアンモニア態窒素をインドフェノール青法で測定した。全リン濃度の測定では、植物生長促進剤A中のリンにモリブデン酸アンモニウムを加えて錯体を形成させ、アスコルビン酸により還元させ、還元反応による生成物の710nmの吸収を測定した。全カリウム濃度は、原子吸光法により測定した。無機窒素は試料4.0gを1.0 M KCl 40mLに溶解させ、遠心分離後の上清を測定に用いた。
[Composition analysis of plant growth promoter A]
The chemical oxygen demand (COD) was measured using a simple COD meter HC-607. The hydrogen ion concentration pH was measured using the glass electrode method according to JIS K0102 17.1. The total carbon concentration was measured using a total organic carbon meter (TOC-V, SSM-5000A, Shimadzu Corporation). In the measurement of total nitrogen concentration, the ammonia nitrogen converted by the Kjeldahl method was measured by the indophenol blue method. In the measurement of the total phosphorus concentration, ammonium molybdate was added to phosphorus in the plant growth promoter A to form a complex, which was reduced by ascorbic acid, and the absorption of the product by the reduction reaction at 710 nm was measured. The total potassium concentration was measured by atomic absorption spectroscopy. For inorganic nitrogen, 4.0 g of the sample was dissolved in 40 mL of 1.0 M KCl, and the supernatant after centrifugation was used for the measurement.
アンモニア態窒素の濃度の測定は、アンモニア態窒素の抽出液1.0mLにフェノールニトロプルシッド溶液400μLを混合し、次亜塩素酸ナトリウム溶液600μLを加えてから撹拌し、45分後に635nmの光の吸光度を分光光度計で測定することにより行った。 To measure the concentration of ammonia nitrogen, mix 400 μL of phenol nitropulside solution with 1.0 mL of ammonia nitrogen extract, add 600 μL of sodium hypochlorite solution, stir, and after 45 minutes, measure the light of 635 nm. This was done by measuring the absorbance with a spectrophotometer.
また、亜硝酸態窒素の濃度の測定では、まず、亜硝酸態窒素の1.0mLの抽出液に100μLのスルファニルアミド溶液を加えてから撹拌し、3分間放置した。その後、ナフチルエチレンジアミン溶液100μLを加えてから撹拌し、20分間放置した。その後、540nmの光の吸光度を分光光度計で測定することにより亜硝酸態窒素の濃度を測定した。 In the measurement of the concentration of nitrite nitrogen, first, 100 μL of sulfanilamide solution was added to 1.0 mL of the extract of nitrite nitrogen, and the mixture was stirred and left for 3 minutes. Then, 100 μL of the naphthylethylenediamine solution was added, and the mixture was stirred and left for 20 minutes. Then, the concentration of nitrite nitrogen was measured by measuring the absorbance of light at 540 nm with a spectrophotometer.
硝酸態窒素の測定では、硝酸態窒素の抽出液200μLにブルシン・4−アミノベンゼンスルホン酸溶液100μLを加えた。その後、硫酸(水:濃硫酸=3:20)1.0mLを加えてから撹拌し、冷暗所で10分間反応させた。さらに水1.0mLを加えた後に、410nmの光の吸光度を分光光度計で測定した。 In the measurement of nitrate nitrogen, 100 μL of a brucine 4-aminobenzenesulfonic acid solution was added to 200 μL of the nitrate nitrogen extract. Then, 1.0 mL of sulfuric acid (water: concentrated sulfuric acid = 3:20) was added, and the mixture was stirred and reacted in a cool and dark place for 10 minutes. After further adding 1.0 mL of water, the absorbance of light at 410 nm was measured with a spectrophotometer.
植物生長促進剤AのpHは8.82、化学的酸素要求量(COD)は749.3±33.4mg/L(試行回数3回、±以下の数値は標準偏差)であった。全炭素濃度は1,100 mg/kg、全窒素濃度は290mg−N/kg、全リン濃度は、26mg/kg、全カリウム濃度は2,700mg/kgであった。水溶性硝酸態窒素濃度は380mg−N/kg、アンモニア性窒素は不検出、水溶性リン酸濃度は五酸化リン酸換算で64mg−P2O5/kg、水溶性カリウム濃度は酸化カリウム換算で3,254mg−K2O/kgであった。 The pH of the plant growth promoter A was 8.82, and the chemical oxygen demand (COD) was 749.3 ± 33.4 mg / L (three trials, values below ± are standard deviations). The total carbon concentration was 1,100 mg / kg, the total nitrogen concentration was 290 mg-N / kg, the total phosphorus concentration was 26 mg / kg, and the total potassium concentration was 2,700 mg / kg. Water-soluble nitrate nitrogen concentration is 380 mg-N / kg, ammoniacal nitrogen is not detected, water-soluble phosphoric acid concentration is 64 mg-P 2 O 5 / kg in terms of pentoxide, and water-soluble potassium concentration is in terms of potassium oxide. It was 3,254 mg-K 2 O / kg.
北海道施肥ガイド2015(北海道ホームページ、 http://www.pref.hokkaido.lg.jp/ns/shs/clean/sehiguide2015.htm、2019年1月21日閲覧)によると、一般的な牛糞堆肥の全炭素量は72,000mg/kg、全窒素量は6,000mg−N/kg、水溶性リン酸は4,000mg−P2O5/kg、水溶性カリウムは5,000mg−K2O/kg程度である。したがって、植物生長促進剤Aの中に含まれる肥料成分は、一般的な牛糞堆肥に比べて極めて希薄であることがわかる。 According to the Hokkaido Fertilization Guide 2015 (Hokkaido homepage, http://www.pref.hokkaido.lg.jp/ns/shs/clean/sehiguide2015.htm, viewed January 21, 2019), all of the general cow dung compost Carbon content is 72,000 mg / kg, total nitrogen content is 6,000 mg-N / kg, water-soluble phosphoric acid is 4,000 mg-P 2 O 5 / kg, and water-soluble potassium is 5,000 mg-K 2 O / kg. Degree. Therefore, it can be seen that the fertilizer component contained in the plant growth promoter A is extremely dilute as compared with general cow dung compost.
[植物生長促進効果の検証(水耕栽培)]
LED光源付の栽培棚でトマト及び小松菜を栽培することにより、植物生長促進効果の確認試験を実施した。試験区では、水で1/10希釈した植物生長促進剤Aを吸収させた約1cm角のウレタンフォームに、種子が上を向いた状態で並べた。一方、比較のための対照区では、脱イオン水を入れたバットに、種子が上を向いた状態で並べた。12時間ごとに光源の点灯状態と消灯状態とを切り替えた。温度の調節は、実験室のエアコンを用いて、28℃に設定することにより行った。それぞれの試験区で27検体の試験を実施し、発芽して生育した植物体の高さを測定し、平均高さ及び標準偏差を求めた。発芽しなかった植物体は実験結果の評価対象から除外した。
[Verification of plant growth promotion effect (hydroponics)]
A confirmation test of the plant growth promoting effect was carried out by cultivating tomatoes and Japanese mustard spinach on a cultivation shelf equipped with an LED light source. In the test plot, the seeds were arranged in a urethane foam of about 1 cm square absorbed with the plant growth promoter A diluted 1/10 with water with the seeds facing upward. On the other hand, in the control group for comparison, the seeds were arranged in a vat containing deionized water with the seeds facing upward. The lighting state and the extinguishing state of the light source were switched every 12 hours. The temperature was adjusted by setting it to 28 ° C. using a laboratory air conditioner. Twenty-seven samples were tested in each test plot, the height of the germinated and grown plants was measured, and the average height and standard deviation were determined. Plants that did not germinate were excluded from the evaluation of experimental results.
図3は、播種後1ヶ月の小松菜及びトマトを撮影した様子を示す写真である。対照区の水のみで生育したトマトならびに小松菜の地上部の高さは、それぞれ1.98±0.13cm、1.93±4.34cmであったのに対し、試験区にて1/10希釈した植物生長促進剤Aで生育したものは、それぞれ7.55±0.86cm、5.04±0.62cmであった。小松菜及びトマトは、試験区においては対照区と比べて、それぞれ3.8倍、2.6倍の高さまで生長した。したがって、製造した植物生長促進剤Aは、小松菜及びトマトの両方において植物生長促進効果をもたらすことを確認できた。 FIG. 3 is a photograph showing a photograph of Japanese mustard spinach and tomatoes one month after sowing. The heights of the above-ground parts of tomatoes and Japanese mustard spinach grown only in the water of the control group were 1.98 ± 0.13 cm and 1.93 ± 4.34 cm, respectively, whereas they were diluted 1/10 in the test group. Those grown with the plant growth promoter A were 7.55 ± 0.86 cm and 5.04 ± 0.62 cm, respectively. Komatsuna and tomato grew to a height of 3.8 times and 2.6 times in the test group as compared with the control group, respectively. Therefore, it was confirmed that the produced plant growth-promoting agent A had a plant growth-promoting effect on both Japanese mustard spinach and tomato.
[実施例2]
[無機栄養源との併用効果]
実施例1と同様の条件で、試験区において、水で500倍希釈したハイポネックス社製のハイポネックス原液(マニュアルの標準使用量。以下、無機栄養とも表記する)と10倍希釈した植物生長促進剤Aとを併用した状態で、トマト及び小松菜を栽培した。対照区において、水で500倍希釈したハイポネックス原液のみを用いて植物生長促進剤Aを加えない状態で、トマト及び小松菜を栽培した。
[Example 2]
[Effect of combined use with inorganic nutrient sources]
Under the same conditions as in Example 1, in the test plot, Hyponex stock solution (standard amount used in the manual; hereinafter also referred to as inorganic nutrition) diluted 500 times with water and plant growth promoter A diluted 10 times. Tomatoes and Komatsuna were cultivated in combination with. In the control group, tomatoes and Japanese mustard spinach were cultivated using only the Hyponex stock solution diluted 500 times with water and without adding the plant growth promoter A.
植物生長促進剤Aを添加せずに無機栄養のみを用いた対照区では、小松菜及びトマトの生長後の高さがそれぞれ5.97±2.4cm、4.70±2.1cmであったのに対し、植物生長促進剤Aと無機栄養を併用した試験区では、それぞれ10.22±5.58cm、4.94±3.28cmであった。小松菜においては約40%の生長促進効果が認められた。トマトを栽培する場合、無機栄養のみの場合と比べて、有意な生長促進効果は認められなかった。以上のように、実施例に記載した植物生長促進剤Aは、市販の肥料と併用する場合に植物の生長促進の相乗効果を発揮することを確認した。 In the control group using only inorganic nutrients without adding the plant growth promoter A, the heights of Japanese mustard spinach and tomato after growth were 5.97 ± 2.4 cm and 4.70 ± 2.1 cm, respectively. On the other hand, in the test group in which the plant growth promoter A and the inorganic nutrient were used in combination, the heights were 10.22 ± 5.58 cm and 4.94 ± 3.28 cm, respectively. In Komatsuna, a growth promoting effect of about 40% was observed. When tomatoes were cultivated, no significant growth promoting effect was observed as compared with the case of using only inorganic nutrients. As described above, it was confirmed that the plant growth promoter A described in the examples exerts a synergistic effect of plant growth promotion when used in combination with a commercially available fertilizer.
[微生物群集解析]
実施例1に記載した方法で製造した植物生長促進剤A(1mL)を遠心分離(20,000×g、5分間)し、沈殿物を回収した。沈殿物を560μLのTE緩衝液(10mM Tris緩衝液(pH8.0)、1mM EDTA)に溶解した後、30μLのSDS溶液、10μLのProteinaseK(10mg/mL)を添加し、混ぜた後、37℃で1時間保温した。その後、100μLの5M NaClを添加し、よく混ぜた後、80μLのCTAB/NaCl溶液を加え、よく混ぜた。サンプルを65℃で10分間保温した。保温後、0.7mLのクロロホルム/イソアミルアルコール(24:1)を添加し、反転混合した。その後、遠心分離(20,000×g、5分間)した。生じた上清を新しいサンプルチューブに移し、フェノールクロロホルム抽出、イソプロパノール沈殿により、DNAを調整した。
[Microbial community analysis]
The plant growth promoter A (1 mL) produced by the method described in Example 1 was centrifuged (20,000 × g, 5 minutes), and the precipitate was collected. The precipitate was dissolved in 560 μL TE buffer (10 mM Tris buffer (pH 8.0), 1 mM EDTA), then 30 μL SDS solution, 10 μL Proteinase K (10 mg / mL) was added, mixed, and then 37 ° C. I kept it warm for 1 hour. Then, 100 μL of 5M NaCl was added and mixed well, then 80 μL of CTAB / NaCl solution was added and mixed well. The sample was kept warm at 65 ° C. for 10 minutes. After heat retention, 0.7 mL of chloroform / isoamyl alcohol (24: 1) was added and inverted and mixed. Then, it was centrifuged (20,000 × g, 5 minutes). The resulting supernatant was transferred to a new sample tube and DNA was prepared by phenol-chloroform extraction and isopropanol precipitation.
分離したDNAを鋳型として、5′-GTCTCGTGGGCTCGGAGATGTGTATAAGAGACAGGACTACHVGGGTATCTAATCC-3′(配列番号4)の塩基配列からなる第1プライマー、及び、5′-TCGTCGGCAGCGTCAGATGTGTATAAGAGACAGCCTACGGGNGGCWGCAG-3′(配列番号3)の塩基配列からなる第2プライマーを用いて、16S rRNAの部分配列を増幅した。具体的には、5 ng/μlのDNA2.5 μlにAmplion PCR Forward Primer (1 μM) 5 μl、Amplicon PCR Reverse Primer (1 μM) 5 μl、KAPA HiFi Hotstart ReadyMix (KAPA Biosystems) 12.5 μlを混合し、サーマルサイクラーT-100 (BioRad)を用いてPCR増幅した。サーマルサイクル反応は初期変性(95℃、3分)の後、変性(95℃、30秒)、アニーリング(55℃、30秒)、伸長反応(72℃、30秒)を25サイクル行い、72℃、5分の伸長反応を行った。 Using the separated DNA as a template, the first primer consisting of the base sequence of 5'-GTCTCGTGGGCTCGGAGATGTGTATAAGAGACAGGACTACHVGGGTATCTAATCC-3'(SEQ ID NO: 4) and the primer consisting of the base sequence of 5'-TCGTCGGCAGCGTCAGATGTGTATAAGACAGCCTACGGGNGGCWGCAG-3' (SEQ ID NO: 3) Was used to amplify a partial sequence of 16S rRNA. Specifically, 5 ng / μl of DNA 2.5 μl was mixed with 5 μl of Amplion PCR Forward Primer (1 μM), 5 μl of Amplifier PCR Reverse Primer (1 μM), and 12.5 μl of KAPA HiFi Hotstart ReadyMix (KAPA Biosystems). , PCR amplification using thermal cycler T-100 (BioRad). In the thermal cycle reaction, after initial denaturation (95 ° C., 3 minutes), denaturation (95 ° C., 30 seconds), annealing (55 ° C., 30 seconds), and extension reaction (72 ° C., 30 seconds) are performed for 25 cycles, and 72 ° C. The elongation reaction was carried out for 5 minutes.
アガロースゲル電気泳動を用いてPCR増幅反応を確認後、AMPure XPビーズを用いて、PCR増幅産物の精製をした。PCR増幅産物を遠心機でスピンダウンした後、ボルテックスでよく撹拌したAMpure XPビーズを20 μl加え、ピペッティングで10回混合した。室温で5分静置後、マグネティックスタンドにセットした状態で2分静置した。その後、透明になった上清をピペッティングで取り除いた。80%エタノールを200 μl加え、30秒静置した。上清を再び取り除き、再度80%エタノールを200 μl加えた。30秒静置後、ピペッティングでエタノールを完全に取り除き、10分風乾した。 After confirming the PCR amplification reaction using agarose gel electrophoresis, the PCR amplification product was purified using AM Pure XP beads. After spinning down the PCR amplification product in a centrifuge, 20 μl of vortex-stirred AMpure XP beads were added and mixed 10 times by pipetting. After allowing to stand at room temperature for 5 minutes, it was allowed to stand for 2 minutes while being set on a magnetic stand. Then, the clear supernatant was removed by pipetting. 200 μl of 80% ethanol was added, and the mixture was allowed to stand for 30 seconds. The supernatant was removed again and 200 μl of 80% ethanol was added again. After allowing to stand for 30 seconds, ethanol was completely removed by pipetting, and the mixture was air-dried for 10 minutes.
続いて、マグネティックスタンドからチューブを取り出し、10 mM Tris-HCl (pH 8.5)を52.5 μl加え、ピペッティングでよく撹拌した。室温で2分静置した後、マグネティックスタンドにセットし、さらに2分静置した。PCR産物が含まれる上清を新しいチューブに移した。Qubit fluorometerを用いて、DNA濃度を確認し、0.2 ng/μl以上であることを確認した。 Subsequently, the tube was removed from the magnetic stand, 52.5 μl of 10 mM Tris-HCl (pH 8.5) was added, and the mixture was well stirred by pipetting. After allowing to stand at room temperature for 2 minutes, it was set on a magnetic stand and allowed to stand for another 2 minutes. The supernatant containing the PCR product was transferred to a new tube. The DNA concentration was confirmed using a Qubit fluorometer, and it was confirmed that the DNA concentration was 0.2 ng / μl or more.
アダプタ及びインデックスを付加するため、2回目のPCRを行った。精製済みのPCR産物5 μlに対してNextera XT Index Primer mix 10 μl、KAPA HiFi HotStart ReadyMix (2 x) 25 μl、RCR grade water 10 μlを混合し、サーマルサイクル反応を行った。サーマルサイクル反応は初期変性(95℃、3分)の後、変性(95℃、30秒)、アニーリング(55℃、30秒)、伸長反応(72℃、30秒)を8サイクル行い、72℃、5分の伸長反応を行った。その後、AMPure XPビーズを用いて、PCR増幅産物の精製をした。更に、Qubit fluorometerを用いて、DNA濃度を確認し、5 ng/μl以上であることを確認した。 A second PCR was performed to add the adapter and index. Nextera XT Index Primer mix 10 μl, KAPA HiFi HotStart ReadyMix (2 x) 25 μl, and RCR grade water 10 μl were mixed with 5 μl of the purified PCR product, and a thermal cycle reaction was carried out. In the thermal cycle reaction, after initial denaturation (95 ° C., 3 minutes), denaturation (95 ° C., 30 seconds), annealing (55 ° C., 30 seconds), and extension reaction (72 ° C., 30 seconds) are carried out for 8 cycles, and 72 ° C. The elongation reaction was carried out for 5 minutes. The PCR amplification product was then purified using AM Pure XP beads. Furthermore, the DNA concentration was confirmed using a Qubit fluorometer, and it was confirmed that the DNA concentration was 5 ng / μl or more.
Illumina社MiSeqシーケンサーを用いて、ペアエンドシークエンスした。得られたリードデータはクオリティーチェック、アダプタならびにインデックス配列を除去し、Qiimeプログラムを用いたクラスター解析に供した。97%以上の相同性に基づくOperated Taxonomic Unit (OTU) を作成し、BLAST解析を用いて、系統学的な情報を付与した。計算過程でOTU代表配列データ、多様性解析データを得た。 Paired-end sequencing was performed using the Illumina MiSeq sequencer. The obtained read data was subjected to quality check, adapter and index sequence removal, and cluster analysis using the Qiime program. An Operated Taxonomic Unit (OTU) based on 97% or more homology was created and phylogenetic information was given using BLAST analysis. OTU representative sequence data and diversity analysis data were obtained during the calculation process.
OTU代表配列データを門レベルでまとめた表を図1に示す。代表配列に含まれるリード数ならびに全リードに対する割合を示している。全リード数は46,605リードであった。アシドバクテリア門に含まれる微生物の割合は14.88%、バクテロイデス門に含まれる微生物の割合は6.804%、クロロビウム門に含まれる微生物の割合は8.619%、クロロフレクサス門に含まれる微生物の割合は8.952%、ゲンマティモナス門に含まれる微生物は3.12%、未培養門OD1に含まれる微生物は2.929%、プランクトミケス門に含まれる微生物は3.525%、プロテオバクテリア門に含まれる微生物は36.792%、ウェルコミクロビウム門に含まれる微生物は2.83%含まれていることを確認した。 A table summarizing the OTU representative sequence data at the phylum level is shown in FIG. The number of reads included in the representative sequence and the ratio to all reads are shown. The total number of leads was 46,605 leads. The proportion of microorganisms contained in the phylum Acidobacteria is 14.88%, the proportion of microorganisms contained in the phylum Bacteroides is 6.804%, the proportion of microorganisms contained in the phylum Chlorobium is 8.619%, and the proportion of microorganisms contained in the phylum Chloroflexus is The ratio of microorganisms is 8.952%, microorganisms contained in the phylum Genmatimonas are 3.12%, microorganisms contained in the uncultivated phylum OD1 are 2.929%, and microorganisms contained in the phylum Proteobacteria are 3.525%. It was confirmed that the microorganisms contained in the phylum Proteobacteria were 36.792% and the microorganisms contained in the phylum Welcomicrobium were 2.83%.
以上、実施形態を用いて本発明を説明したが、本発明の技術的範囲は上記実施の形態に記載の範囲には限定されず、その要旨の範囲内で種々の変形及び変更が可能である。例えば、装置の全部又は一部は、任意の単位で機能的又は物理的に分散・統合して構成することができる。また、複数の実施の形態の任意の組み合わせによって生じる新たな実施の形態も、本発明の実施の形態に含まれる。組み合わせによって生じる新たな実施の形態の効果は、もとの実施の形態の効果を併せ持つ。 Although the present invention has been described above using the embodiments, the technical scope of the present invention is not limited to the scope described in the above embodiments, and various modifications and changes can be made within the scope of the gist thereof. .. For example, all or a part of the device can be functionally or physically distributed / integrated in any unit. Also included in the embodiments of the present invention are new embodiments resulting from any combination of the plurality of embodiments. The effect of the new embodiment produced by the combination has the effect of the original embodiment.
本実施形態の植物生長促進剤は、植物の生長を促進するので、農作物の収穫量を増加させることができる。 Since the plant growth promoter of the present embodiment promotes the growth of plants, the yield of agricultural products can be increased.
10 糞尿貯め
20 供給部
30a 第1曝気処理槽
30b 第2曝気処理槽
30c 第3曝気処理槽
30d 第4曝気処理槽
50 回収部
100 製造装置
10 Manure storage 20 Supply unit 30a 1st aeration treatment tank 30b 2nd aeration treatment tank 30c 3rd aeration treatment tank 30d 4th aeration treatment tank 50 Recovery unit 100 Manufacturing equipment
Claims (9)
植物生長促進剤。 A plant growth promoter made from livestock manure, from microorganisms contained in the phylum Bacteroidetes, microorganisms contained in the phylum Chloroflexi, microorganisms contained in the phylum Gemmatimonadetes, and microorganisms contained in the phylum Verrucomicrobia. Includes at least one or more of the group
Plant growth promoter.
請求項1に記載の植物生長促進剤。 A first primer containing the nucleotide sequence shown by 5'-CCTACGGGNGGCWGCAG-3'(SEQ ID NO: 1) (in the nucleotide sequence, N is A, T, G or C, and W is A or T) and 5 Using a second primer containing the base sequence shown by ′-GACTACHVGGGTATCTAATCC-3 ′ (SEQ ID NO: 2) (in the base sequence, H is A, T or C and V is A, C or G). When the microorganism contained in the plant growth promoter is detected, the microorganism contained in the phylum Bacteroidetes, the microorganism contained in the phylum Chloroflexi, the microorganism contained in the phylum Gemmatimonadetes, and the phylum Verrucomicrobia At least one or more of the group consisting of the contained microorganisms is detected.
The plant growth promoter according to claim 1.
請求項1又は2に記載の植物生長促進剤。 Total carbon concentration is 2,000 mg / kg or less,
The plant growth promoter according to claim 1 or 2.
請求項1〜3のいずれか一項に記載の植物生長促進剤。 The total nitrogen concentration measured by the Kjeldahl method is 500 mg / kg or less.
The plant growth promoter according to any one of claims 1 to 3.
請求項1〜4のいずれか一項に記載の植物生長促進剤。 Total phosphorus concentration is 2,000 mg / kg or less,
The plant growth promoter according to any one of claims 1 to 4.
請求項1〜5のいずれか一項に記載の植物生長促進剤。 Total potassium concentration is 5,000 mg / kg or less,
The plant growth promoter according to any one of claims 1 to 5.
請求項1〜6のいずれか一項に記載の植物生長促進剤。 The plant growth promoter is in the form of a liquid, solid or slurry.
The plant growth promoter according to any one of claims 1 to 6.
5′-CCTACGGGNGGCWGCAG-3′(配列番号1)の塩基配列を含む第1プライマーと5′-GACTACHVGGGTATCTAATCC-3′(配列番号2)の塩基配列を含む第2プライマーとを用いて検出される微生物のうち、バクテロイデス門に含まれる微生物を1.5%以上、クロロフレクサス門に含まれる微生物を1.5%以上、ゲンマティモナス門に含まれる微生物を0.5%以上、及び、ウェルコミクロビウム門に含まれる微生物からなる群のうち少なくとも1種以上を0.5%以上含むようになるまで、前記液体成分を曝気させるステップとを含む、
植物生長促進剤の製造方法。 Steps to separate the liquid components of livestock manure,
Microorganisms detected using the first primer containing the nucleotide sequence of 5'-CCTACGGGNGGCWGCAG-3'(SEQ ID NO: 1) and the second primer containing the nucleotide sequence of 5'-GACTACHVGGGTATCTAATCC-3'(SEQ ID NO: 2) Of these, 1.5% or more of the microorganisms contained in the phylum Bacteroidetes, 1.5% or more of the microorganisms contained in the phylum Chloroflexi, 0.5% or more of the microorganisms contained in the phylum Gemmatimonadetes, and Welcomicrobium. A step of exposing the liquid component to 0.5% or more of at least one of the group of microorganisms contained in the phylum is included.
A method for producing a plant growth promoter.
を満たす状態において前記液体成分を曝気させる、
請求項8に記載の植物生長促進剤の製造方法。 In the aeration step, when F [m / s] is the air flow rate, V [m 3 ] is the treatment liquid volume, and H L [m] is the treatment liquid depth.
The liquid component is aerated in a state satisfying the above conditions.
The method for producing a plant growth promoter according to claim 8.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2019038319A JP7485272B2 (en) | 2019-03-04 | 2019-03-04 | Plant Growth Promoters |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2019038319A JP7485272B2 (en) | 2019-03-04 | 2019-03-04 | Plant Growth Promoters |
Publications (2)
Publication Number | Publication Date |
---|---|
JP2020141564A true JP2020141564A (en) | 2020-09-10 |
JP7485272B2 JP7485272B2 (en) | 2024-05-16 |
Family
ID=72352943
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2019038319A Active JP7485272B2 (en) | 2019-03-04 | 2019-03-04 | Plant Growth Promoters |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP7485272B2 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP7148099B1 (en) | 2021-07-19 | 2022-10-05 | 環境大善株式会社 | Method for producing plant growth promoter, method for producing microalgae growth promoter, and method for producing fulvic acid-containing liquid |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2008303122A (en) * | 2007-06-08 | 2008-12-18 | Murata Kensetsu:Kk | Soil, plant growth conditioning material |
JP2009057235A (en) * | 2007-08-31 | 2009-03-19 | Kurarisu Kankyo Kk | Method for producing compost |
JP2012041210A (en) * | 2010-08-16 | 2012-03-01 | Kurarisu Kankyo Kk | Method for producing liquid fertilizer |
JP2015167912A (en) * | 2014-03-07 | 2015-09-28 | 南 尚 | Livestock excreta treating system |
CN106497926A (en) * | 2016-11-03 | 2017-03-15 | 承启医学(深圳)科技有限公司 | A kind of amplicon primer and construction method for building microbial bacterial 16s rDNA variable regions sequencing library |
JP2019500905A (en) * | 2016-01-05 | 2019-01-17 | ウェルミクロ ソチエタ レスポンサビリタ リミタータWellmicro S.R.L. | Evaluation method of individual health |
-
2019
- 2019-03-04 JP JP2019038319A patent/JP7485272B2/en active Active
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2008303122A (en) * | 2007-06-08 | 2008-12-18 | Murata Kensetsu:Kk | Soil, plant growth conditioning material |
JP2009057235A (en) * | 2007-08-31 | 2009-03-19 | Kurarisu Kankyo Kk | Method for producing compost |
JP2012041210A (en) * | 2010-08-16 | 2012-03-01 | Kurarisu Kankyo Kk | Method for producing liquid fertilizer |
JP2015167912A (en) * | 2014-03-07 | 2015-09-28 | 南 尚 | Livestock excreta treating system |
JP2019500905A (en) * | 2016-01-05 | 2019-01-17 | ウェルミクロ ソチエタ レスポンサビリタ リミタータWellmicro S.R.L. | Evaluation method of individual health |
CN106497926A (en) * | 2016-11-03 | 2017-03-15 | 承启医学(深圳)科技有限公司 | A kind of amplicon primer and construction method for building microbial bacterial 16s rDNA variable regions sequencing library |
Non-Patent Citations (6)
Title |
---|
APPL ENVIRON MICROBIOL., vol. 73, no. 1, JPN6023001036, 2007, pages 193 - 202, ISSN: 0005091221 * |
ARCH. MICROBIOL., vol. 198, JPN6023025016, 23 June 2016 (2016-06-23), pages 987 - 993, ISSN: 0005091223 * |
ECO-ENGINEERING, vol. 19, no. 4, JPN6023001032, 2007, pages 239 - 245, ISSN: 0005091218 * |
ECOLOGICAL ENGINEERING, vol. 81, JPN6023001038, 2015, pages 363 - 372, ISSN: 0005091222 * |
J APPL MICROBIOL., vol. 111, JPN6023001035, 2011, pages 1416 - 1425, ISSN: 0005091220 * |
J ENVIRON SCI., vol. 22, no. 5, JPN6023001033, 2010, pages 656 - 662, ISSN: 0005091219 * |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP7148099B1 (en) | 2021-07-19 | 2022-10-05 | 環境大善株式会社 | Method for producing plant growth promoter, method for producing microalgae growth promoter, and method for producing fulvic acid-containing liquid |
JP2023014446A (en) * | 2021-07-19 | 2023-01-31 | 環境大善株式会社 | Production method of plant growth accelerating agent, production method of microalgae growth accelerating agent, and production method of fulvic acid-containing liquid |
Also Published As
Publication number | Publication date |
---|---|
JP7485272B2 (en) | 2024-05-16 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Bei et al. | Response of the soil microbial community to different fertilizer inputs in a wheat-maize rotation on a calcareous soil | |
Suleiman et al. | From toilet to agriculture: Fertilization with microalgal biomass from wastewater impacts the soil and rhizosphere active microbiomes, greenhouse gas emissions and plant growth | |
US8962336B2 (en) | Soil diagnosis and improvement method | |
Nahar et al. | Levels of heavy metal concentrations and their effect on net nitrification rates and nitrifying archaea/bacteria in paddy soils of Bangladesh | |
Wang et al. | Insights into the role of plant on ammonia-oxidizing bacteria and archaea in the mangrove ecosystem | |
Zarezadeh et al. | Microalgae and phototrophic purple bacteria for nutrient recovery from agri-industrial effluents: influences on plant growth, rhizosphere bacteria, and putative carbon-and nitrogen-cycling genes | |
Yu et al. | Changes in abundance and composition of nitrifying communities in barley (Hordeum vulgare L.) rhizosphere and bulk soils over the growth period following combined biochar and urea amendment | |
Ishikawa et al. | Denitrification in soil amended with thermophile-fermented compost suppresses nitrate accumulation in plants | |
Luchibia et al. | Responses of ureolytic and nitrifying microbes to urease and nitrification inhibitors in selected agricultural soils in Victoria, Australia | |
Cloutier et al. | Tillage intensity and plant rhizosphere selection shape bacterial-archaeal assemblage diversity and nitrogen cycling genes | |
Zhang et al. | Effects of organic fertilizers on yield, soil physico-chemical property, soil microbial community diversity and structure of Brassica rapa var. Chinensis | |
Qing et al. | Profiles of tetracycline resistance genes in paddy soils with three different organic fertilizer applications | |
Montoya et al. | Nitrous oxide emissions and microbial communities during the transition to conservation agriculture using N-enhanced efficiency fertilisers in a semiarid climate | |
Candra et al. | Response of growth and production of shallot (Allium ascalonicum L.) to liquid fertilizer and cattle manure. | |
JP2013022293A (en) | Environment improvement material | |
Bossolani et al. | Nitrogen input on organic amendments alters the pattern of soil–microbe-plant co-dependence | |
JP7485272B2 (en) | Plant Growth Promoters | |
Guo et al. | Rhizosphere microbiome-related changes in soil zinc and phosphorus availability improve grain zinc concentration of wheat | |
Carreras-Sempere et al. | The use of recovered struvite and ammonium nitrate in fertigation in a horticultural rotation: agronomic and microbiological assessment | |
WO2021066115A1 (en) | Use of microorganism to improve plant productivity of soil | |
Liu et al. | Winter cover crops alter methanotrophs community structure in a double-rice paddy soil | |
Pholkaw et al. | Utilization of wood biomass for organic soil based on the soil fertility index (SOFIX) | |
Lin et al. | The mechanism of using magnetized-ionized water in combination with organic fertilizer to enhance soil health and cotton yield | |
WO2021215439A1 (en) | Microalgae growth promoter and method for producing microalgae growth promoter | |
Shalmani et al. | Influence of 3, 4-dimethylpyrazole phosphate as a nitrification inhibitor on nitrogen dynamics in different wheat varieties by the isotopes |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20220201 |
|
A711 | Notification of change in applicant |
Free format text: JAPANESE INTERMEDIATE CODE: A712 Effective date: 20220928 |
|
A977 | Report on retrieval |
Free format text: JAPANESE INTERMEDIATE CODE: A971007 Effective date: 20221228 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20221226 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20230124 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20230324 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20230627 |
|
A601 | Written request for extension of time |
Free format text: JAPANESE INTERMEDIATE CODE: A601 Effective date: 20230823 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20231019 |
|
RD02 | Notification of acceptance of power of attorney |
Free format text: JAPANESE INTERMEDIATE CODE: A7422 Effective date: 20231019 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20231219 |
|
RD03 | Notification of appointment of power of attorney |
Free format text: JAPANESE INTERMEDIATE CODE: A7423 Effective date: 20240131 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20240214 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A821 Effective date: 20240201 |
|
TRDD | Decision of grant or rejection written | ||
A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20240416 |
|
A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20240422 |
|
R150 | Certificate of patent or registration of utility model |
Ref document number: 7485272 Country of ref document: JP Free format text: JAPANESE INTERMEDIATE CODE: R150 |