JPH0710229B2 - Method for growing soil microorganisms - Google Patents
Method for growing soil microorganismsInfo
- Publication number
- JPH0710229B2 JPH0710229B2 JP20697491A JP20697491A JPH0710229B2 JP H0710229 B2 JPH0710229 B2 JP H0710229B2 JP 20697491 A JP20697491 A JP 20697491A JP 20697491 A JP20697491 A JP 20697491A JP H0710229 B2 JPH0710229 B2 JP H0710229B2
- Authority
- JP
- Japan
- Prior art keywords
- soil microorganisms
- soil
- microorganisms
- growth medium
- gelled
- 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.)
- Expired - Fee Related
Links
- 239000002689 soil Substances 0.000 title claims description 111
- 244000005700 microbiome Species 0.000 title claims description 102
- 238000000034 method Methods 0.000 title claims description 8
- 239000001963 growth medium Substances 0.000 claims description 31
- 239000011324 bead Substances 0.000 claims description 30
- 239000000284 extract Substances 0.000 claims description 22
- 230000000717 retained effect Effects 0.000 claims description 19
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 16
- 239000007864 aqueous solution Substances 0.000 claims description 15
- 239000003864 humus Substances 0.000 claims description 12
- 230000000813 microbial effect Effects 0.000 claims description 11
- 239000002609 medium Substances 0.000 claims description 10
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 9
- IXPNQXFRVYWDDI-UHFFFAOYSA-N 1-methyl-2,4-dioxo-1,3-diazinane-5-carboximidamide Chemical compound CN1CC(C(N)=N)C(=O)NC1=O IXPNQXFRVYWDDI-UHFFFAOYSA-N 0.000 claims description 8
- 229910052742 iron Inorganic materials 0.000 claims description 8
- 235000010413 sodium alginate Nutrition 0.000 claims description 8
- 239000000661 sodium alginate Substances 0.000 claims description 8
- 229940005550 sodium alginate Drugs 0.000 claims description 8
- -1 iron ions Chemical class 0.000 claims description 7
- 229910021645 metal ion Inorganic materials 0.000 claims description 7
- 239000000203 mixture Substances 0.000 claims description 6
- 239000002244 precipitate Substances 0.000 claims description 4
- 239000011148 porous material Substances 0.000 claims description 3
- 238000003756 stirring Methods 0.000 claims description 2
- 239000002781 deodorant agent Substances 0.000 description 25
- 230000001877 deodorizing effect Effects 0.000 description 19
- GETQZCLCWQTVFV-UHFFFAOYSA-N trimethylamine Chemical compound CN(C)C GETQZCLCWQTVFV-UHFFFAOYSA-N 0.000 description 14
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 13
- 239000001110 calcium chloride Substances 0.000 description 13
- 229910001628 calcium chloride Inorganic materials 0.000 description 13
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 11
- 239000007788 liquid Substances 0.000 description 7
- 239000000243 solution Substances 0.000 description 7
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 6
- GUBGYTABKSRVRQ-QKKXKWKRSA-N Lactose Natural products OC[C@H]1O[C@@H](O[C@H]2[C@H](O)[C@@H](O)C(O)O[C@@H]2CO)[C@H](O)[C@@H](O)[C@H]1O GUBGYTABKSRVRQ-QKKXKWKRSA-N 0.000 description 6
- 241000209094 Oryza Species 0.000 description 6
- 235000007164 Oryza sativa Nutrition 0.000 description 6
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- 229940041514 candida albicans extract Drugs 0.000 description 6
- 239000008101 lactose Substances 0.000 description 6
- 235000009566 rice Nutrition 0.000 description 6
- 230000035943 smell Effects 0.000 description 6
- 239000012138 yeast extract Substances 0.000 description 6
- 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
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 5
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 5
- 235000011130 ammonium sulphate Nutrition 0.000 description 5
- 238000001914 filtration Methods 0.000 description 5
- 239000000499 gel Substances 0.000 description 5
- 239000008103 glucose Substances 0.000 description 5
- 238000005507 spraying Methods 0.000 description 5
- 238000012360 testing method Methods 0.000 description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- 229910021529 ammonia Inorganic materials 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 239000007789 gas Substances 0.000 description 4
- 239000012528 membrane Substances 0.000 description 4
- 241000251468 Actinopterygii Species 0.000 description 3
- 235000010410 calcium alginate Nutrition 0.000 description 3
- 239000000648 calcium alginate Substances 0.000 description 3
- 229960002681 calcium alginate Drugs 0.000 description 3
- OKHHGHGGPDJQHR-YMOPUZKJSA-L calcium;(2s,3s,4s,5s,6r)-6-[(2r,3s,4r,5s,6r)-2-carboxy-6-[(2r,3s,4r,5s,6r)-2-carboxylato-4,5,6-trihydroxyoxan-3-yl]oxy-4,5-dihydroxyoxan-3-yl]oxy-3,4,5-trihydroxyoxane-2-carboxylate Chemical compound [Ca+2].O[C@@H]1[C@H](O)[C@H](O)O[C@@H](C([O-])=O)[C@H]1O[C@H]1[C@@H](O)[C@@H](O)[C@H](O[C@H]2[C@H]([C@@H](O)[C@H](O)[C@H](O2)C([O-])=O)O)[C@H](C(O)=O)O1 OKHHGHGGPDJQHR-YMOPUZKJSA-L 0.000 description 3
- 239000003795 chemical substances by application Substances 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 229910052757 nitrogen Inorganic materials 0.000 description 3
- 230000035755 proliferation Effects 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- 238000001179 sorption measurement Methods 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 229920000742 Cotton Polymers 0.000 description 2
- VSCWAEJMTAWNJL-UHFFFAOYSA-K aluminium trichloride Chemical compound Cl[Al](Cl)Cl VSCWAEJMTAWNJL-UHFFFAOYSA-K 0.000 description 2
- 238000004332 deodorization Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000011325 microbead Substances 0.000 description 2
- 239000011259 mixed solution Substances 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 230000000644 propagated effect Effects 0.000 description 2
- 239000010865 sewage Substances 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- QJZYHAIUNVAGQP-UHFFFAOYSA-N 3-nitrobicyclo[2.2.1]hept-5-ene-2,3-dicarboxylic acid Chemical compound C1C2C=CC1C(C(=O)O)C2(C(O)=O)[N+]([O-])=O QJZYHAIUNVAGQP-UHFFFAOYSA-N 0.000 description 1
- GUBGYTABKSRVRQ-XLOQQCSPSA-N Alpha-Lactose Chemical compound O[C@@H]1[C@@H](O)[C@@H](O)[C@@H](CO)O[C@H]1O[C@@H]1[C@@H](CO)O[C@H](O)[C@H](O)[C@H]1O GUBGYTABKSRVRQ-XLOQQCSPSA-N 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 108010028690 Fish Proteins Proteins 0.000 description 1
- CZMRCDWAGMRECN-UGDNZRGBSA-N Sucrose Chemical compound O[C@H]1[C@H](O)[C@@H](CO)O[C@@]1(CO)O[C@@H]1[C@H](O)[C@@H](O)[C@H](O)[C@@H](CO)O1 CZMRCDWAGMRECN-UGDNZRGBSA-N 0.000 description 1
- 229930006000 Sucrose Natural products 0.000 description 1
- 239000001166 ammonium sulphate Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- WQZGKKKJIJFFOK-VFUOTHLCSA-N beta-D-glucose Chemical compound OC[C@H]1O[C@@H](O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-VFUOTHLCSA-N 0.000 description 1
- 210000000988 bone and bone Anatomy 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 238000001879 gelation Methods 0.000 description 1
- 239000010800 human waste Substances 0.000 description 1
- 239000004021 humic acid Substances 0.000 description 1
- 210000003692 ilium Anatomy 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 235000013372 meat Nutrition 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 230000002062 proliferating effect Effects 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 238000002791 soaking Methods 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 239000005720 sucrose Substances 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Landscapes
- Cultivation Of Plants (AREA)
- Immobilizing And Processing Of Enzymes And Microorganisms (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Description
【0001】[0001]
【産業上の利用分野】この発明は、土壌微生物の特性を
利用してこれを脱臭剤として使用する場合において、脱
臭剤に使用する土壌微生物を自然土壌に含まれる個数の
数千倍〜数万倍に増殖させて、脱臭効能を高め、又脱臭
剤の使用期間を長くし、更に、少ない脱臭剤の使用量で
必要な脱臭効能を得ることができ、しかも、土壌微生物
を繁殖させて無尽蔵に土壌微生物を生成することのでき
る土壌微生物の増殖方法に関するものである。This invention relates to the use of soil microorganisms as a deodorant by utilizing the characteristics of the soil microorganisms. It can be doubled to enhance the deodorizing effect, extend the period of use of the deodorant, and obtain the necessary deodorizing effect with a small amount of the deodorant used. The present invention relates to a method for growing soil microorganisms capable of producing soil microorganisms.
【0002】[0002]
【従来の技術】従来、悪臭を除去する脱臭剤として、例
えば、悪臭成分を物理的に吸着する活性炭等を利用す吸
着型脱臭剤、悪臭成分と化学的に反応して、臭気成分を
補足する化学的脱臭剤、または、微生物の悪臭に対する
資化作用を利用した生物学的な脱臭剤などが知られてい
る2. Description of the Related Art Conventionally, as a deodorant for removing a malodor, for example, an adsorption type deodorant utilizing activated carbon that physically adsorbs a malodorous component, and chemically reacting with the malodorous component to supplement the malodorous component. Chemical deodorants or biological deodorants that utilize the assimilation action against the malodor of microorganisms are known.
【0003】このうち、活性炭等の物理的吸着力を利用
するものでは、悪臭成分の吸着が飽和するとそれ以上の
効果は期待できず、その都度、新しい脱臭脱臭剤を用い
る必要がある。また、化学的脱臭は、速効性であるもの
の、一時的なものであり、長期に有効なものはなく、ま
た使用するものによって環境汚染等の問題がある。[0003] Of these, the one utilizing the physical adsorption force of activated carbon or the like cannot expect any further effect when the adsorption of the malodorous component is saturated, and it is necessary to use a new deodorizing deodorant each time. Further, although chemical deodorization is quick-acting, it is temporary and is not effective for a long period of time, and there is a problem such as environmental pollution depending on what is used.
【0004】これに対して、生物学的脱臭剤は、速効性
且つ永続的であることが期待されている。そして、土壌
微生物を抽出して脱臭剤とした発明としては、例えば特
開昭62−297288(『腐植質脱臭剤による家畜ふ
ん尿、し尿、下水ならびに魚腸骨等処理場の悪臭ガスの
肥料化方法』)などが公開されている。In contrast, biological deodorants are expected to be fast acting and permanent. And as an invention for extracting soil microorganisms as a deodorant, for example, Japanese Patent Laid-Open No. 62-297288 (“Method for fertilizing offensive odor gas from a sewage treatment plant such as livestock manure, human waste, sewage and fish ilium with a humus deodorant” )) Etc. have been published.
【0005】[0005]
【発明が解決しようとする課題】ところで、土壌1g中
に含まれる微生物の数は土壌及び微生物の種類によって
その上限があり、このため、土壌から微生物を抽出した
場合、微生物の最大数には限りがある。The number of microorganisms contained in 1 g of soil has an upper limit depending on the type of soil and microorganisms. Therefore, when microorganisms are extracted from soil, the maximum number of microorganisms is limited. There is.
【0006】他方、脱臭効能は、微生物の数にある程度
比例し、また、脱臭剤の使用量も微生物の数に比例し、
更に、脱臭剤の使用期間も微生物の数にある程度比例す
ると考えられるから、脱臭剤中に含まれる微生物はでき
るだけその数が多い方が望ましい。On the other hand, the deodorizing effect is proportional to the number of microorganisms to some extent, and the amount of the deodorant used is also proportional to the number of microorganisms.
Further, since the period of use of the deodorant is considered to be proportional to the number of microorganisms to some extent, it is desirable that the number of microorganisms contained in the deodorant be as large as possible.
【0007】また、土壌微生物を生成するためには、腐
植から土壌微生物を抽出しなければならず、このために
は、土壌微生物を含んだ腐植をその都度確保しなければ
ならず、その腐植の入手作業が面倒である等の不都合も
ある。Further, in order to generate soil microorganisms, it is necessary to extract soil microorganisms from the humus, and for this purpose, it is necessary to secure a humus containing soil microorganisms each time. There are also inconveniences such as troublesome acquisition work.
【0008】この発明は、上記のような課題に鑑み、そ
の課題を解決すべく創案されたものであって、その目的
とするところは、土壌微生物の特性を利用してこれを脱
臭剤として使用する場合において、脱臭剤に使用する土
壌微生物を自然土壌に含まれる個数の数千倍〜数万倍に
増殖させて、脱臭効能を高め、又脱臭剤の使用期間を長
くし、更に、少ない脱臭剤の使用量で必要な脱臭効能を
得ることができ、しかも、土壌微生物を繁殖させること
によって、無尽蔵に土壌微生物を生成することのできる
土壌微生物の増殖方法を提供することにある。The present invention was made in view of the above problems and was devised to solve the problems. The object of the present invention is to utilize the characteristics of soil microorganisms as a deodorant. In this case, the soil microbes used in the deodorant are grown to a number of thousands to tens of thousands of times the number contained in natural soil to enhance the deodorizing effect, and the deodorant is used for a longer period of time, and further, a small amount of deodorant is used. It is an object of the present invention to provide a method for proliferating soil microorganisms, which can obtain the required deodorizing effect with the use amount of the agent and can reproduce the soil microorganisms inexhaustibly to produce the soil microorganisms.
【0009】[0009]
【課題を解決するための手段】以上の目的を達成するた
めに、請求項1に係る発明は、土壌微生物を含む腐植に
水を混合した後、これを濾過して得た土壌微生物抽出液
にアルカリ水溶液を入れてpHを調整して土壌微生物抽
出液中の鉄イオンなどを沈澱させ、これを濾過して沈澱
物を除去し、これにアルギン酸ナトリウム水溶液を加え
て攪拌混合してゾル状態の土壌微生物抽出液を作り、こ
のゾル状態の土壌微生物抽出液を細孔から2〜3価の金
属イオンを含有する水溶液中に滴下して表面をゲル化し
たビーズ状の内部に土壌微生物を留め、表面をゲル化し
たビーズ状の内部に留められた土壌微生物を2〜3価の
金属イオンを含有する増殖用培地中に放置して、内部ま
でゲル化したビーズ状の内部に留められた土壌微生物の
濃度を高める方法よりなるものである。To achieve the above object, the invention according to claim 1 provides a soil microorganism extract obtained by mixing humus containing soil microorganisms with water and filtering the mixture. An alkaline aqueous solution is added to adjust the pH to precipitate iron ions and the like in the soil microbial extract, the precipitate is removed by filtration, and the sodium alginate aqueous solution is added to this to stir and mix the soil in the sol state. A microbial extract is made, and this sol-state soil microbial extract is dripped from the pores into an aqueous solution containing divalent and trivalent metal ions to retain the gel on the inside of the bead-like gelled surface. The bead-shaped soil microorganisms retained inside the gel are left in a medium for growth containing a divalent or trivalent metal ion, and the bead-like soil microorganisms that have been gelled to the inside How to increase the concentration It is Li Cheng thing.
【0010】また、請求項2に係る発明は、請求項1の
ゲル化したビーズ状の内部に留められた土壌微生物を増
殖用培地中に放置して、ビーズ中の土壌微生物を増殖用
培地中に放出させ、増殖用培地中の土壌微生物の濃度を
高める方法よりなるものである。Further, the invention according to claim 2 is that the soil microorganisms retained inside the gelled bead-like interior of claim 1 are left in the growth medium to allow the soil microorganisms in the beads to grow in the growth medium. To increase the concentration of soil microorganisms in the growth medium.
【0011】[0011]
【作用】以上のような構成を有するこの発明は、次のよ
うに作用する。すなわち、請求項1に係る発明によれ
ば、ゲル化したビーズ状の内部に留められた土壌微生物
は数千〜数万倍に増殖されるので、この増殖されたビー
ズ状の土壌微生物を脱臭剤として使用した場合には、増
殖してないものに比べて、土壌微生物の数が数千〜数万
倍も多いため、脱臭効能を高め、又脱臭剤の使用期間を
長くし、更に、少ない脱臭剤の使用量で必要な脱臭効能
を得ることができるように作用する。The present invention having the above-described structure operates as follows. That is, according to the invention of claim 1, since the gelled bead-shaped soil microorganisms retained inside are grown several thousand to tens of thousands times, the grown bead-shaped soil microorganisms are deodorized. When used as a product, the number of soil microorganisms is several thousand to tens of thousands times higher than that of non-grown ones, increasing the deodorizing effect and extending the period of use of the deodorizing agent, and further reducing deodorization. It acts so that the required deodorizing effect can be obtained with the amount of the agent used.
【0012】また、請求項2に係る発明によれば、ゲル
化したビーズ状の内部に留められた土壌微生物を増殖さ
せる増殖用培地に土壌微生物が繁殖するので、この増殖
用培地で繁殖された土壌微生物を使ってゲル化したビー
ズ状の内部に留められた土壌微生物を繁殖させることが
でき、このため、最初だけ腐植から土壌微生物を抽出
し、その後はこれを繰り返すのみで、無尽蔵に脱臭剤の
原料となる土壌微生物を生成することができるように作
用する。According to the second aspect of the present invention, since the soil microorganisms propagate in the medium for growth that grows the soil microorganisms retained inside the gelled bead, the medium for growth is propagated. The soil microorganisms can be used to propagate the gel microorganisms that are retained inside the gelled bead, so that the soil microorganisms can be extracted from the humus only for the first time, and then this can be repeated indefinitely. It acts so as to be able to produce soil microorganisms that are the raw material of.
【0013】[0013]
【実施例】以下、実施例に基づいてこの発明をより具体
的に説明する。EXAMPLES The present invention will be described in more detail based on the following examples.
【0014】〔第1実施例〕土壌微生物を含む腐植(フ
ミン酸)と水を重量比で、1:2の割合で、腐植に水を
入れて十分に混合する。この場合、使用する水は、例え
ば蒸留後、イオン交換された純水が好ましい。[First Example] Humus (humic acid) containing soil microorganisms and water were mixed at a weight ratio of 1: 2 by adding water to the humus. In this case, the water used is preferably pure water that has been ion-exchanged after distillation.
【0015】そして、腐植と水を十分に混合し、1日間
経過後、腐植と水の混合液を濾過する。濾過は2回行わ
れ、1回目はガーゼなどを使用した荒濾過で、大粒の土
の除去し、2回目は荒濾過で濾過された混合液を濾紙1
種を使用して濾過して、土壌微生物抽出液を得る。この
土壌微生物抽出液はpH2〜3の酸性を示す。Then, the humus and water are thoroughly mixed, and after 1 day, the mixed solution of humus and water is filtered. Filtration is carried out twice, the first time is rough filtration using gauze or the like to remove large particles of soil, and the second time is the mixed solution filtered by rough filtration with filter paper 1
Filter using seeds to obtain a soil microbial extract. This soil microbial extract exhibits an acidity of pH 2-3.
【0016】この土壌微生物抽出液中には鉄イオンが溶
解しているので、この鉄イオンを除去する必要があり、
このため、希水酸化ナトリウム溶液を土壌微生物抽出液
に混入してpH調整を行い、略中性のpH7になるよう
に調整する。この希水酸化ナトリウム溶液の混入によ
り、鉄イオンなどが沈澱する。Since iron ions are dissolved in the soil microorganism extract, it is necessary to remove the iron ions.
Therefore, the diluted sodium hydroxide solution is mixed with the soil microbial extract to adjust the pH so that the pH becomes substantially neutral. By mixing this dilute sodium hydroxide solution, iron ions and the like precipitate.
【0017】鉄イオンなどが沈澱したら、この土壌微生
物抽出液を濾紙1種で濾過して、鉄イオンなどの沈澱物
を除去して、中和土壌微生物抽出液を得る。この中和土
壌微生物抽出液には1g当り106 〜107 個の土壌微
生物が存在している。When iron ions and the like are precipitated, the soil microorganism extract is filtered with one kind of filter paper to remove precipitates such as iron ions to obtain a neutralized soil microorganism extract. This neutralized soil microorganism extract contains 10 6 to 10 7 soil microorganisms per 1 g.
【0018】次に、中和土壌微生物抽出液に、例えば容
積で同量のアルギン酸ナトリウム4%水溶液を混入して
完全に均一になるように十分に攪拌混合して、2%アル
ギン酸ナトリウム・中和土壌微生物抽出液が得られる。
このアルギン酸ナトリウム・中和土壌微生物抽出液はゾ
ル状態にある。Next, the neutralized soil microbial extract is mixed with, for example, the same volume of a 4% aqueous solution of sodium alginate, and the mixture is sufficiently stirred and mixed so as to be completely homogeneous, and 2% sodium alginate neutralized. A soil microbial extract is obtained.
This sodium alginate / neutralized soil microorganism extract is in a sol state.
【0019】続いて、ゾル状態のアルギン酸ナトリウム
・中和土壌微生物抽出液を細孔から、例えば2%塩化カ
ルシウム水溶液へ滴下する。この場合、塩化カルシウム
水溶液に代えて、例えば塩化アルミニウムでもよく、要
は2〜3価の金属イオンを含有する溶液であればよい。
また、その溶液の濃度は例えば2%以上あるのが好まし
い。Then, the sol-state sodium alginate / neutralized soil microorganism extract is added dropwise from the pores to, for example, a 2% calcium chloride aqueous solution. In this case, for example, aluminum chloride may be used instead of the calcium chloride aqueous solution, and the point is that it is a solution containing divalent to trivalent metal ions.
The concentration of the solution is preferably 2% or more.
【0020】塩化カルシウム水溶液へ滴下したゾル状態
のアルギン酸ナトリウム・中和土壌微生物抽出液は、そ
の表面が塩化カルシウム水溶液と反応して、その表面が
半透膜のアルギン酸カルシウムに変わりゲル化される。
このようにして、土壌微生物抽出液は塩化カルシウム水
溶液内で、表面全体がゲル化された半透膜なアルギン酸
カルシウムで覆われたビーズ状となり、そのビーズ状の
内部に土壌微生物が留められる。The surface of the sol-state sodium alginate / neutralized soil microbial extract dropped into the aqueous solution of calcium chloride reacts with the aqueous solution of calcium chloride, and the surface thereof becomes a semipermeable membrane of calcium alginate and is gelled.
In this way, the soil microorganisms extract is in the form of beads covered with semipermeable membrane calcium alginate whose entire surface is gelled in the calcium chloride aqueous solution, and the soil microorganisms are retained inside the beads.
【0021】塩化カルシウム水溶液中には滴下して生成
された多数の内部に土壌微生物を留めたビーズ状のもの
が得られる。この多数のビーズを塩化カルシウム水溶液
中から取り出す。取り出しは例えばザルなどを使って行
い、取り出し後、水洗いなどによってビーズの表面の塩
化カルシウムを洗い流す。この水洗い作業は必要に応じ
て省略してもよい。In the calcium chloride aqueous solution, a bead-like substance in which soil microorganisms are retained inside a large number of drops produced is obtained. The large number of beads are taken out from the calcium chloride aqueous solution. For example, a colander is used for taking out, and after taking out, the calcium chloride on the surface of the beads is washed away by washing with water. This washing operation may be omitted if necessary.
【0022】このようにして生成されたビーズ中には1
g当り106 〜107 個の土壌微生物が存在している
が、土壌微生物の働きを高めるために、このビーズ中に
含まれる土壌微生物の数を更に数千倍〜数万倍に増や
す。1 is contained in the beads thus produced.
Although 10 6 to 10 7 soil microorganisms are present per g, the number of soil microorganisms contained in the beads is further increased to several thousand to several ten thousand times in order to enhance the function of the soil microorganisms.
【0023】しかも、このとき、この内部に土壌微生物
を留めるビーズをそのまま脱臭剤などに使用する場合、
ビーズ表面の膜が破れて内部の土壌微生物が流出するの
を防ぐために、ビーズの内部までゲル化する。このた
め、内部に土壌微生物を留めたビーズを2〜3価の金属
イオンを含有する増殖用培地中に放置して増殖する。In addition, at this time, when the beads for retaining soil microorganisms inside are directly used as a deodorant, etc.,
In order to prevent the membrane on the bead surface from breaking and the soil microorganisms inside to flow out, gelation is performed inside the beads. For this reason, the beads in which soil microorganisms are retained inside are left to proliferate in a growth medium containing a divalent to trivalent metal ion.
【0024】増殖用培地は、例えば、糖と酵母エキス、
糖と米糠、糖と油粕などの組み合わせの完全培地からな
る。また、糖には例えばグルコース、乳糖、蔗糖などが
使用される。これに、2〜3価の金属イオンである例え
ば塩化カルシウムが加えられ、更に、硫安なども適宜加
えられている。また、その組成の比率として、例えば、
酵母エキス1%、乳糖5%、硫安1%、塩化カルシウム
0.1%、残りは水分、の組み合わせものがある。硫安は
必要に応じて省略してもよい。The growth medium is, for example, sugar and yeast extract,
It consists of a complete medium consisting of sugar and rice bran and sugar and oil cake. Further, as the sugar, for example, glucose, lactose, sucrose and the like are used. To this, for example, calcium chloride, which is a divalent to trivalent metal ion, is added, and further ammonium sulfate or the like is also added as appropriate. Also, as the composition ratio, for example,
Yeast extract 1%, lactose 5%, ammonium sulfate 1%, calcium chloride
There is a combination of 0.1% and the rest is water. Ammonium sulfate may be omitted if necessary.
【0025】そして、上記の酵母エキス1%、乳糖5
%、硫安1%、塩化カルシウム 0.1%、残りは水分、の
組成の培地中に、内部に土壌微生物を留めたビーズを1
夜間(16時間程度)放置すると、塩化カルシウムによ
ってビーズ内部のアルギン酸ナトリウムがアルギン酸カ
ルシウムに置換されて、ビーズの内部までゲル化され
る。そして、この間に、ビーズ1g当りの土壌微生物の
数は1010〜1011個に増加し、ビーズ中に含まれる土
壌微生物の数は数千倍〜数万倍、増えている。Then, 1% of the above yeast extract and 5 lactose
%, Ammonium sulphate 1%, calcium chloride 0.1%, the rest is water.
When left overnight (about 16 hours), calcium chloride replaces sodium alginate inside the beads with calcium alginate, and gels inside the beads. During this period, the number of soil microorganisms per 1 g of beads has increased to 10 10 to 10 11 and the number of soil microorganisms contained in the beads has increased several thousand to several tens of thousands of times.
【0026】〔第2実施例〕第1実施例の製法によって
生成したゲル化したビーズ状の内部に留められた土壌微
生物を増殖用培地中に放置すると、ビーズ中の土壌微生
物の一部はゲル化した半透膜を通過して増殖用培地中に
出て、増殖用培地中に土壌微生物が生存する。そして、
土壌微生物はその増殖用培地中で増殖され、増殖用培地
中の土壌微生物の濃度が高まる。[Second Example] When the soil microorganisms retained in the gelled bead-like interior produced by the production method of the first embodiment are left in the growth medium, a part of the soil microorganisms in the beads is gelled. The soil microorganisms survive in the growth medium by passing through the converted semipermeable membrane into the growth medium. And
The soil microorganisms are grown in the growth medium, increasing the concentration of soil microorganisms in the growth medium.
【0027】〔増殖用培地と土壌微生物のビーズの関
係〕増殖用培地中の土壌微生物の濃度は、増殖用培地の
成分、増殖用培地中に放置する土壌微生物のビーズの量
などによって、次のようになる。なお、増殖用培地は酵
母エキスとグルコースを用いた。また、6日間増殖後の
土壌微生物の数を測定した。 上記の結果から、ビーズ量40%(培地500mlに対し
て200g)〜5%(培地500mlに対して25g)で
は、土壌微生物の増殖個数に大差がないことが認められ
る。また、グルコース量も、12%〜3%の範囲では土
壌微生物の増殖個数に大差がないことが認められる。[Relationship Between Growth Medium and Soil Microbeads] The concentration of soil microorganisms in the growth medium depends on the components of the growth medium, the amount of soil microorganisms beads left in the growth medium, and the like. Like The growth medium used was yeast extract and glucose. In addition, the number of soil microorganisms after 6 days of growth was measured. From the above results, it is recognized that there is no great difference in the growth number of soil microorganisms when the amount of beads is 40% (200 g for 500 ml of medium) to 5% (25 g for 500 ml of medium). In addition, it is recognized that there is no great difference in the growth number of soil microorganisms when the glucose amount is in the range of 12% to 3%.
【0028】〔増殖用培地の組成〕増殖用培地を組成す
るグルコースおよび酵母エキスの代わりに乳糖および米
糠を使用して増殖を行った場合には、次のようになる。
なお、米糠は粉末でこのまま使用すると、増殖タンクを
汚染する可能性があるので、米糠200gを1リットル
の水液中に1夜間浸漬した後、米糠を濾過した米糠抽出
液を増殖用培地に供した。また、ビーズ400gを増殖
用培地1リットルに入れ、24時間経過後の土壌微生物
の個数を測定した。 ここで、米糠抽出液(ml)および乳糖(g)は増殖用培
地1リットル中に含まれる量であり、残りは水分であ
る。[Composition of Medium for Proliferation] When lactose and rice bran are used in place of glucose and yeast extract which constitute the medium for proliferation, the following is performed.
If rice bran is powdered and used as it is, it may contaminate the growth tank. Therefore, after soaking 200 g of rice bran in 1 liter of water solution for one night, the rice bran extract is used as a growth medium. did. In addition, 400 g of beads was placed in 1 liter of a growth medium, and the number of soil microorganisms after 24 hours was counted. Here, the rice bran extract (ml) and the lactose (g) are contained in 1 liter of the growth medium, and the rest is water.
【0029】この土壌微生物が生存している増殖用培地
は、前記の第1実施例の土壌微生物を内部に留めたゲル
化したビーズを製造する場合の原料として使用され、ま
た、土壌微生物を含んだ脱臭液として使用される。この
場合、増殖を繰り返すことによって、土壌微生物を腐植
から抽出する作業を不要にでき、しかも、工業的に土壌
微生物を生成することが可能となる。The growth medium in which the soil microorganisms are alive is used as a raw material in the case of producing the gelled beads having the soil microorganisms retained therein according to the first embodiment, and contains the soil microorganisms. It is used as a deodorizing solution. In this case, by repeating the multiplication, the work of extracting the soil microorganisms from the humus can be eliminated, and the soil microorganisms can be industrially produced.
【0030】〔効能試験〕第1実施例で製造された土壌
微生物を内部に留めたビーズ、及び第2実施例で製造さ
れた土壌微生物が生存する増殖用培地の液体を、脱臭剤
として使用したときの脱臭効能を調べたものである。な
お、第1実施例の土壌微生物を内部に留めたビーズの製
造条件は、酵母エキス1%、乳糖5%、硫安1%、塩化
カルシウム 0.1%、残りは水分、の組成の培地中に、内
部に土壌微生物を留めたビーズを1夜間(16時間程
度)放置して、増殖および内部までゲル化したものであ
る。また、第2実施例の土壌微生物が生存する増殖用培
地の液体の製造条件は、培地液500mlに酵母エキス1
%、グルコース6%の組成中で、土壌微生物のビーズ1
00gを6日間増殖させたものである。[Efficacy test] The beads in which the soil microorganisms produced in the first example were retained, and the liquid of the growth medium in which the soil microorganisms produced in the second example survived were used as deodorants. The deodorizing effect at that time was investigated. In addition, the production conditions of the beads in which the soil microorganisms of the first example are retained inside are as follows: yeast extract 1%, lactose 5%, ammonium sulfate 1%, calcium chloride 0.1%, the rest is water. The beads on which soil microorganisms were retained were left to stand overnight (about 16 hours) to grow and gel inside. In addition, the production conditions of the liquid of the growth medium in which the soil microorganisms of the second embodiment survive are as follows:
%, Glucose 6%, soil microbeads 1
00g was grown for 6 days.
【0031】(1)アンモニア アンモニアに対する脱臭効能を、図1に図示する。 ここで、aは第1実施例のビーズ40gをにおい袋に入
れた後、窒素ベースのアンモニアガス(1000ppm)を3リ
ットル封入した場合である。 bは第2実施例の増殖用培地の液体50mlを脱脂綿に吸
着させたものをにおい袋に入れた後、窒素ベースのアン
モニアガス(1000ppm)を3リットル封入した場合であ
る。 cは何も入れてないにおい袋に、窒素ベースのアンモニ
アガス(1000ppm)を3リットル封入した場合である。 図1より、アンモニアに対する脱臭効能はかなり高いこ
とが認められる。(1) Ammonia The deodorizing effect on ammonia is shown in FIG. Here, a is the case where 40 g of the beads of the first embodiment were put in an odor bag and then 3 liters of nitrogen-based ammonia gas (1000 ppm) was enclosed. In b, 50 ml of the liquid of the growth medium of the second embodiment is adsorbed on absorbent cotton, put into an odor bag, and then 3 liters of nitrogen-based ammonia gas (1000 ppm) is enclosed. c is a case where 3 liters of nitrogen-based ammonia gas (1000 ppm) is enclosed in an odor bag containing nothing. From FIG. 1, it is recognized that the deodorizing effect on ammonia is considerably high.
【0032】(2)トリメチルアミン トリメチルアミンに対する脱臭効能を、図1に図示す
る。 ここで、aは第1実施例のビーズ40gをにおい袋に入
れた後、トリメチルアミンガス(1000ppm)を3リットル
封入した場合である。 bは第2実施例の増殖用培地の液体50mlを脱脂綿に吸
着させたものをにおい袋に入れた後、トリメチルアミン
ガス(1000ppm)を3リットル封入した場合である。 cは何も入れてないにおい袋に、トリメチルアミンガス
(1000ppm)を3リットル封入した場合である。 図2より、トリメチルアミンに対する脱臭効能はかなり
高いことが認められる。(2) Trimethylamine The deodorizing effect on trimethylamine is shown in FIG. Here, a is the case where 40 g of the beads of the first embodiment were put in an odor bag and then 3 liters of trimethylamine gas (1000 ppm) was enclosed. b is a case where 50 ml of the liquid of the growth medium of the second embodiment is adsorbed on absorbent cotton, put into an odor bag, and then 3 liters of trimethylamine gas (1000 ppm) is enclosed. c is a case where 3 liters of trimethylamine gas (1000 ppm) is enclosed in an odor bag containing nothing. From FIG. 2, it is recognized that the deodorizing effect on trimethylamine is considerably high.
【0033】(3)豚舎臭気除去試験 第2実施例の増殖用培地の液体1リットルを1トン水槽
に入れ、1000倍液としたものを、豚舎具備のシャワ
ースプレーで豚舎全体に2時間間隔で2日間散布した。
散布開始の翌日、臭気は激減した。(3) Pig-house odor removal test A liquid of 1 liter of the growth medium of the second embodiment was placed in a 1 ton water tank to prepare a 1000-fold solution, which was sprayed on the whole pig-house at 2-hour intervals with a shower spray provided in the pig-house. Sprayed for 2 days.
The day after the start of spraying, the odor dropped dramatically.
【0034】(4)汲み取り式トイレ脱臭試験 第2実施例の増殖用培地の液体20mlを水1リットルに
溶かし、トイレ内槽に如雨露を用いて万遍なく散布し
た。約1時間後、臭気はなくなった。その後、30日間
効果は持続中である。(4) Sucking-up type toilet deodorizing test 20 ml of the growth medium liquid of the second example was dissolved in 1 liter of water, and sprayed evenly in the toilet tank using rain and dew. After about 1 hour, the odor disappeared. After that, the effect continues for 30 days.
【0035】(5)水産加工工場臭気除去試験 第2実施例の増殖用培地の液体を、希釈倍率1000倍
と500倍に薄めたものについて試験した。試験場所は
次の箇所で行った。 C級原魚室────−5度Cの冷蔵庫で広さ約300m
2 。 残滓缶────鉄製箱(1m×1m×1m)。残滓は魚
の身以外の全て(内蔵や骨、頭など)。 ロータリスクリーン部────廃水処理第1段階の荒ご
み回収装置。小屋式で二方開放。 スクリュープレス部────廃水中のタンパク回収装
置。80〜90度C程度の魚肉タンパク泥が残滓缶と同
じ大きさのタンクに常時ベルトコンベアで供給される。 臭気の評価基準は次のとおりである。 『5』────強く臭う。 『4』────やや強く臭う。 『3』────普通に臭う。 『2』────かすかに臭う。 『1』────臭わない。 『?』────臭うか臭わないかわからない。(5) Deodorizing test for fisheries processing plant The liquid of the growth medium of the second example was diluted with 1000 times and 500 times and tested. The test location was as follows. Class C raw fish room ──── -5 degree C refrigerator about 300m wide
2 . Remains can ──── Iron box (1m x 1m x 1m). Remains are all except fish meat (internal, bone, head, etc.). Rotary screen ──── Wastewater treatment first-stage waste collection device. Opened in two ways in a hut style. Screw press section ──── Protein recovery device for wastewater. The fish protein mud of about 80 to 90 degrees C is constantly supplied to the tank of the same size as the residual can by the belt conveyor. The odor evaluation criteria are as follows. "5" --- It smells strongly. “4” ──── It smells a little strongly. "3" --- It smells normally. "2" --- It smells faint. "1" --- Doesn't smell. "? I don't know if it smells or not.
【0036】 ここで、7月11日午前10時に散布を行った。また、
その全面に散布を行い、その使用量は全面散布に必要な
量だけ散布した。[0036] Here, spraying was performed at 10 am on July 11th. Also,
The entire surface was sprayed, and the amount used was the amount necessary for spraying the entire surface.
【0037】 ここで、7月16日午前10時に散布を行った。また、
その全面に散布を行い、その使用量は全面散布に必要な
量だけ散布した。[0037] Here, spraying was performed at 10 am on July 16th. Also,
The entire surface was sprayed, and the amount used was the amount necessary for spraying the entire surface.
【0038】なお、この発明は上記実施例に限定される
ものではなく、この考案の精神を逸脱しない範囲で種々
の改変をなし得ることは勿論である。The present invention is not limited to the above embodiments, and it goes without saying that various modifications can be made without departing from the spirit of the invention.
【0039】[0039]
【発明の効果】以上の記載より明らかなように、請求項
1の発明に係る土壌微生物の増殖方法によれば、ゲル化
したビーズ状の内部に留められた土壌微生物は数千〜数
万倍に増殖されるので、この増殖されたビーズ状の土壌
微生物を脱臭剤として使用した場合には、増殖してない
ものに比べて、土壌微生物の数が数千〜数万倍も多いた
め、脱臭効能を高め、又脱臭剤の使用期間を長くし、更
に、少ない脱臭剤の使用量で必要な脱臭効能を得ること
ができる。As is apparent from the above description, according to the method for growing soil microorganisms according to the invention of claim 1, the number of soil microorganisms retained inside the gelled bead is several thousand to several ten thousand times. When used as a deodorant, the beaded soil microorganisms that have proliferated in this way are deodorized because the number of soil microorganisms is thousands to tens of thousands of times greater than that of non-proliferated soil microorganisms. The effect can be enhanced, the period of use of the deodorant can be extended, and the required deodorant effect can be obtained with a small amount of the deodorant used.
【0040】また、請求項2の発明に係る土壌微生物の
増殖方法によれば、ゲル化したビーズ状の内部に留めら
れた土壌微生物を増殖させる増殖用培地に土壌微生物が
繁殖するので、この増殖用培地で繁殖された土壌微生物
を使ってゲル化したビーズ状の内部に留められた土壌微
生物を繁殖させることができ、このため、最初だけ腐植
から土壌微生物を抽出し、その後はこれを繰り返すのみ
で、無尽蔵に脱臭剤の原料となる土壌微生物を生成する
ことができるという、極めて新規的有益なる効果を奏す
るものである。According to the method for growing soil microorganisms according to the second aspect of the present invention, since the soil microorganisms propagate in the medium for growing the soil microorganisms retained inside the gelled bead-shaped interior, the proliferation of the soil microorganisms occurs. It is possible to propagate the soil microorganisms retained inside the gelled bead using the soil microorganisms propagated in the culture medium, so only the soil microorganisms are first extracted from the humus, and then this is repeated. Thus, it is possible to produce soil microorganisms, which are the raw material of the deodorant, inexhaustibly, and there is an extremely new and beneficial effect.
【図1】アンモニアに対する脱臭効能を示す図である。FIG. 1 is a diagram showing a deodorizing effect on ammonia.
【図2】トリメチルアミンに対する脱臭効能を示す図で
ある。FIG. 2 is a diagram showing the deodorizing effect on trimethylamine.
Claims (2)
後、これを濾過して得た土壌微生物抽出液にアルカリ水
溶液を入れてpHを調整して土壌微生物抽出液中の鉄イ
オンなどを沈澱させ、これを濾過して沈澱物を除去し、
これにアルギン酸ナトリウム水溶液を加えて攪拌混合し
てゾル状態の土壌微生物抽出液を作り、このゾル状態の
土壌微生物抽出液を細孔から2〜3価の金属イオンを含
有する水溶液中に滴下して表面をゲル化したビーズ状の
内部に土壌微生物を留め、表面をゲル化したビーズ状の
内部に留められた土壌微生物を2〜3価の金属イオンを
含有する増殖用培地中に放置して、内部までゲル化した
ビーズ状の内部に留められた土壌微生物の濃度を高める
ことを特徴とする土壌微生物の増殖方法。1. A mixture of water to a humus containing soil microorganisms, which is then filtered to obtain an aqueous solution of soil microorganisms, the pH of which is adjusted by adding an alkaline aqueous solution to precipitate iron ions and the like in the soil microorganism extract. And filtered to remove the precipitate,
An aqueous solution of sodium alginate is added to this and mixed with stirring to prepare a soil microbial extract in the sol state, and the soil microbial extract in the sol state is dropped from the pores into an aqueous solution containing divalent to trivalent metal ions. Soil microorganisms are retained inside the beaded surface gelled, and the soil microorganisms retained inside the beaded surface gelled are left to stand in a growth medium containing 2-3 valent metal ions, A method for growing soil microorganisms, which comprises increasing the concentration of soil microorganisms retained inside a bead-like gel that has gelled to the inside.
留められた土壌微生物を増殖用培地中に放置して、ビー
ズ中の土壌微生物を増殖用培地中に放出させ、増殖用培
地中の土壌微生物の濃度を高めることを特徴とする土壌
微生物の増殖方法。2. The gelled bead-shaped soil microorganisms of claim 1 are allowed to stand in a growth medium to release the soil microorganisms in the beads into the growth medium, and the medium is grown in the growth medium. A method for growing soil microorganisms, which comprises increasing the concentration of soil microorganisms.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP20697491A JPH0710229B2 (en) | 1991-08-19 | 1991-08-19 | Method for growing soil microorganisms |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP20697491A JPH0710229B2 (en) | 1991-08-19 | 1991-08-19 | Method for growing soil microorganisms |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0549468A JPH0549468A (en) | 1993-03-02 |
| JPH0710229B2 true JPH0710229B2 (en) | 1995-02-08 |
Family
ID=16532084
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP20697491A Expired - Fee Related JPH0710229B2 (en) | 1991-08-19 | 1991-08-19 | Method for growing soil microorganisms |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0710229B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2018168046A (en) * | 2017-03-30 | 2018-11-01 | 宇部興産株式会社 | Cement clinker manufacturing method and cement manufacturing method |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP6548124B2 (en) * | 2015-09-01 | 2019-07-24 | 学校法人甲南学園 | A culture solution for mulberry cultivation, a culture medium for mulberry cultivation, a method for producing a culture liquid for mulberry cultivation, and a cultivation method for mulberry |
| JP7471908B2 (en) * | 2020-05-14 | 2024-04-22 | 株式会社レゾナック・テクノサービス | Method for manufacturing seedling soil, seedling soil, and method for cultivating plants |
-
1991
- 1991-08-19 JP JP20697491A patent/JPH0710229B2/en not_active Expired - Fee Related
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2018168046A (en) * | 2017-03-30 | 2018-11-01 | 宇部興産株式会社 | Cement clinker manufacturing method and cement manufacturing method |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0549468A (en) | 1993-03-02 |
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