JP2015231351A - Bag-shaped microbial preparation in which sulfur bacteria are carried, and environmental purification method using the same - Google Patents

Bag-shaped microbial preparation in which sulfur bacteria are carried, and environmental purification method using the same Download PDF

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JP2015231351A
JP2015231351A JP2014119821A JP2014119821A JP2015231351A JP 2015231351 A JP2015231351 A JP 2015231351A JP 2014119821 A JP2014119821 A JP 2014119821A JP 2014119821 A JP2014119821 A JP 2014119821A JP 2015231351 A JP2015231351 A JP 2015231351A
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JP5855704B2 (en
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良治 佐伯
Ryoji Saeki
良治 佐伯
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/20Sludge processing

Abstract

PROBLEM TO BE SOLVED: To provide a microbial preparation used for purification of water quality, decomposition of sludge, soil improvement or the like which does not require a large-scale apparatus, has excellent dispersibility and can be used simply and quickly, and in which sulfur bacteria are carried stably so as to exert purification capability.SOLUTION: There is provided a powdery microbial preparation in which a carrier containing neutral porous particles having a particle size of 50 μm or less by 70 vol.% or more is allowed to carry sulfur bacteria. Further, there is also provided a bag-shaped microbial preparation in which silica sand and white sand are mixed into the powdery microbial preparation, and which is encapsulated into a bag having water permeability.

Description

本発明は、水質浄化やヘドロの改質等に使用される微生物製剤及び袋状微生物製剤ならびにそれらを用いた環境浄化方法に関する。この微生物製剤は、硫黄細菌が担持されており、かつ粒子サイズが小さい多孔質粒子を微生物担体として用いるものである。   The present invention relates to a microbial preparation and a bag-shaped microbial preparation used for water purification, sludge modification, and the like, and an environmental purification method using them. This microbial preparation uses porous particles carrying sulfur bacteria and having a small particle size as a microbial carrier.

従来、河川や湖沼などの水質を浄化するための方法として、様々な技術が開発されており、例えば、各種代謝による浄化能を示す微生物を用いた処理方法が知られている。   Conventionally, various techniques have been developed as methods for purifying water quality such as rivers and lakes. For example, treatment methods using microorganisms that exhibit purification ability by various metabolisms are known.

従来から用いられている微生物を用いた処理方法により一定の水質の浄化効果等が確認されているが、排水管や側溝、くみ取り式トイレ等のアンモニア、硫化水素、メルカプタンなどの、悪臭やヘドロの原因物質に対する効果は十分なものとは言えない。これは、微生物を用いた処理方法といっても、どのような微生物を選択的に増殖させるような処理方法を行うかによって、その効果が全く異なるからである。微生物による浄化時に重要な元素としては、炭素(C)、水素(H)、酸素(O)、窒素(N)、リン(P)が生体構成源として比率が多いことから、これらの除去を目的とした設計が行われることが多く、有機物の主たる元素である炭素の除去、さらには高度浄化として、窒素、リンを除去するための各種好気性細菌、嫌気性細菌が検討されてきたが、これらのみでは十分ではない場合がある。   The treatment method using microorganisms that have been used in the past has been confirmed to have a certain level of water purification effect, but it does not cause bad odors or sludge such as ammonia, hydrogen sulfide, mercaptans, etc. The effect on the causative substance is not sufficient. This is because even if it is a treatment method using microorganisms, the effect is completely different depending on which treatment method selectively propagates microorganisms. As elements important for purification by microorganisms, carbon (C), hydrogen (H), oxygen (O), nitrogen (N), and phosphorus (P) have a large ratio as biological constituents. In many cases, various aerobic and anaerobic bacteria for removing nitrogen and phosphorus have been studied for removal of carbon, which is the main element of organic matter, and for advanced purification. Sometimes it is not enough.

従来達成できなかったような、更なる高度浄化を行うためには、元素として硫黄(S)を含む物質を代謝し無害化することができる菌を利用する方法がある。このような硫黄を代謝する菌としては、硫黄細菌が知られている。この硫黄細菌を利用した水質浄化技術としては、例えば、特許文献1〜3が開示されている。特許文献1に開示された技術は、廃水中の有機物を硫酸塩還元反応槽で熱交換器によって加温しながら硫酸塩還元菌により酸化するとともに硫酸イオン及び硫黄を還元する工程と、硫黄脱窒槽で硫黄脱窒細菌により還元硫黄の脱窒を行う工程と、硝化槽で硝化細菌により硝化を行う工程と、残部を固液分離して上澄液を放流する工程と、上記硫酸塩還元反応槽の排ガス中に含まれている硫化水素を硫黄酸化槽に導いて、水蒸気源により加温しながら硫黄酸化槽内で硫黄酸化細菌によって硫化水素を酸化して硫酸を生成する工程と、該硫黄酸化槽内の液のpHを調節した後、硫酸塩還元反応に必要とする硫酸イオンを硫酸塩還元反応槽に還流する工程とを備えている。また、特許文献2に開示された技術は、熱交換器の有無や、水蒸気による加温の有無等について異なるものの特許文献1と類似する技術である。また、特許文献3に開示された技術は、特許文献1に開示された技術と、二酸化炭素の有無、熱交換器の有無、沈殿槽の明確な規定等において異なるものの、硫黄細菌等を利用し、硫黄還元、硫黄脱窒、硝化、固液分離、排ガス処理等の構成を有する点で類似する技術である。   In order to perform further advanced purification that could not be achieved in the past, there is a method of utilizing bacteria capable of metabolizing and detoxifying substances containing sulfur (S) as an element. Sulfur bacteria are known as such bacteria that metabolize sulfur. For example, Patent Documents 1 to 3 are disclosed as water purification technologies using sulfur bacteria. The technique disclosed in Patent Document 1 includes a step of oxidizing an organic substance in wastewater by a sulfate-reducing bacterium while heating it with a heat exchanger in a sulfate reduction reaction tank and reducing sulfate ions and sulfur, and a sulfur denitrification tank. A step of denitrifying reduced sulfur with a sulfur denitrifying bacterium, a step of nitrifying with a nitrifying bacterium in a nitrifying tank, a step of solid-liquid separating the remainder and discharging the supernatant, and the sulfate reduction reaction tank Introducing hydrogen sulfide contained in the exhaust gas into a sulfur oxidation tank, oxidizing the hydrogen sulfide by sulfur-oxidizing bacteria in the sulfur oxidation tank while heating with a water vapor source, and producing the sulfuric acid And adjusting the pH of the solution in the tank, and then refluxing sulfate ions required for the sulfate reduction reaction to the sulfate reduction reaction tank. Moreover, the technique disclosed in Patent Document 2 is similar to that of Patent Document 1 although it differs with respect to the presence or absence of a heat exchanger, the presence or absence of heating with water vapor, and the like. In addition, the technique disclosed in Patent Document 3 differs from the technique disclosed in Patent Document 1 in the presence or absence of carbon dioxide, the presence or absence of a heat exchanger, the clear regulation of the sedimentation tank, etc., but uses sulfur bacteria or the like. This technology is similar in that it has configurations such as sulfur reduction, sulfur denitrification, nitrification, solid-liquid separation, and exhaust gas treatment.

また、微生物を利用するにあたっては、微生物を担体に担持させた固定床型の浄化方法が知られている。この担体としては様々なものが知られているが、例えば特許文献4にはフライアッシュ系の多孔質セラミックスを用いるもの、特許文献5にはPVA等を用いたゲル担体を用いたもの、特許文献6にはヤシガラを用いたものなどが開示されている。   Moreover, when using microorganisms, a fixed bed type purification method in which microorganisms are supported on a carrier is known. Various carriers are known. For example, Patent Document 4 uses a fly ash type porous ceramic, Patent Document 5 uses a gel carrier using PVA, Patent Document 5 6 discloses a method using coconut shells.

特開平05−234322号公報JP 05-234322 A 特開平05−228493号公報JP 05-228493 A 特開平05−115897号公報Japanese Patent Laid-Open No. 05-115897 特開平11−292654号公報JP 11-292654 A 特許第3241950号公報Japanese Patent No. 3241950 特開平09−75971号公報JP 09-75971 A

特許文献1〜3に開示された技術では、いずれも大掛かりな装置が必要となり、従来その処理が困難であったヘドロ等の簡易迅速な分解は困難であった。また、微生物の担体に特徴を有する特許文献4〜6に開示された技術は、いずれも、使用環境の制限が大きく、広域の浄化が求められるような池や海に用いるには分散性が悪いなどの問題があった。また、硫黄細菌の担体として用いると硫黄細菌が担持されにくかったり、成長し難かったり死滅したりするため定着性が低いものであった。このような環境下、本発明は、大規模な装置を必要とすることなく、分散性に優れ簡易迅速に使用でき、かつ安定して浄化能を奏するように硫黄細菌が担持された微生物製剤を提供することを課題とする。   The techniques disclosed in Patent Documents 1 to 3 all require a large-scale device, and it is difficult to easily and quickly disassemble sludge or the like that has been difficult to process. In addition, any of the techniques disclosed in Patent Documents 4 to 6 characterized by a carrier for microorganisms has a very limited use environment and is poorly dispersible for use in ponds and seas that require purification over a wide area. There were problems such as. In addition, when used as a carrier for sulfur bacteria, the sulfur bacteria are difficult to be supported, difficult to grow, or die, and thus have low fixability. Under such circumstances, the present invention provides a microbial preparation on which sulfur bacteria are supported so that they can be used easily and quickly with excellent dispersibility and stably purify without requiring a large-scale apparatus. The issue is to provide.

本発明者は、上記課題を解決すべく鋭意研究を重ねた結果、下記の発明が上記目的に合致することを見出し、本発明に至った。   As a result of intensive studies to solve the above problems, the present inventor has found that the following inventions meet the above object, and have reached the present invention.

すなわち、本発明は、以下の発明に係るものである。
<1> 粒子サイズ50μm以下の中性の多孔質粒子を70容量%以上含む担体に、硫黄細菌を担持させた粉体状微生物製剤。
<2> さらに好気性細菌および/または通性嫌気性細菌を混合させた前記<1>記載の粉体状微生物製剤。
<3> 前記多孔質粒子が、モンモリロナイトおよびゼオライト、カオリンからなる群から選択される少なくとも1種以上である前記<1>または<2>に記載の粉体状微生物製剤
<4> 前記<1>〜<3>のいずれかに記載の粉体状微生物製剤に、珪砂及び白砂を混合し、通水性を有する袋に封入した袋状微生物製剤。
<5> 封入に用いられる前記袋が生分解性不織布製である前記<4>記載の袋状微生物製剤。
<6> 前記<1>〜<5>のいずれかに記載の粉体状微生物製剤および/または袋状微生物製剤を用いた、水の浄化、ヘドロの分解、土壌改良、消臭およびプランクトン発生抑制から選択される少なくとも1以上の環境浄化方法。
That is, the present invention relates to the following inventions.
<1> A powdery microbial preparation in which sulfur bacteria are supported on a carrier containing 70% by volume or more of neutral porous particles having a particle size of 50 μm or less.
<2> The powdery microbial preparation according to the above <1>, further mixed with aerobic bacteria and / or facultative anaerobic bacteria.
<3> The powdery microorganism preparation according to <1> or <2>, wherein the porous particles are at least one selected from the group consisting of montmorillonite, zeolite, and kaolin <4> The above <1> A bag-like microbial preparation obtained by mixing silica sand and white sand with the powdered microbial preparation according to any one of <3> and enclosing it in a water-permeable bag.
<5> The bag-like microorganism preparation according to <4>, wherein the bag used for encapsulation is made of a biodegradable nonwoven fabric.
<6> Water purification, sludge decomposition, soil improvement, deodorization, and plankton generation suppression using the powdery microorganism preparation and / or the bag-like microorganism preparation according to any one of <1> to <5> One or more environmental purification methods selected from.

本発明の微生物製剤は、硫黄細菌を担持するものであり、分散性に優れ簡易迅速に使用でき、かつ安定した硫黄細菌による浄化能を奏するものである。この微生物製剤は、例えば、水の浄化やヘドロの分解、土壌改良、消臭、プランクトンの発生抑制に効果を奏する。   The microbial preparation of the present invention carries sulfur bacteria, has excellent dispersibility, can be used easily and quickly, and exhibits a purification ability with stable sulfur bacteria. This microbial preparation is effective in, for example, purification of water, decomposition of sludge, soil improvement, deodorization, and suppression of plankton generation.

以下に本発明の実施の形態を詳細に説明するが、以下に記載する構成要件の説明は、本発明の実施態様の一例(代表例)であり、本発明はその要旨を超えない限り、以下の内容に限定されない。   DESCRIPTION OF EMBODIMENTS Embodiments of the present invention will be described in detail below. However, the description of the constituent elements described below is an example (representative example) of an embodiment of the present invention. It is not limited to the contents.

本発明は、粒子サイズ50μm以下の中性の多孔質粒子を70容量%以上含む担体に、硫黄細菌を担持させた粉体状微生物製剤に関するものである。この微生物製剤は、分散性等に優れており、汚染環境などに硫黄細菌を効率的に付与することに適した態様であり、適宜、各種環境に存在する菌等との相乗効果を奏することで水の浄化、ヘドロの分解、土壌改良、消臭、プランクトンの発生抑制に効果を奏する。   The present invention relates to a powdery microbial preparation in which sulfur bacteria are supported on a carrier containing neutral porous particles having a particle size of 50 μm or less in an amount of 70% by volume or more. This microbial preparation is excellent in dispersibility, etc., and is a mode suitable for efficiently imparting sulfur bacteria to contaminated environments, etc., and by appropriately producing a synergistic effect with bacteria present in various environments. It is effective for water purification, sludge decomposition, soil improvement, deodorization, and plankton generation suppression.

本発明の微生物製剤は、粒子サイズ50μm以下の中性の多孔質粒子を70容量%以上含む担体を用いるものである。微生物製剤とは、微生物を利用して各種機能を奏するものの総称であり、より具体的には担体に微生物を担持させて利用されるものを指す。   The microorganism preparation of the present invention uses a carrier containing 70% by volume or more of neutral porous particles having a particle size of 50 μm or less. The microbial preparation is a general term for substances that exhibit various functions using microorganisms, and more specifically, refers to those that are used by supporting microorganisms on a carrier.

本発明の微生物製剤には多孔質粒子を主とした担体を用いる。多孔質粒子とは、粒子内に多くの細孔を有する粒子である。例えばケイ酸塩鉱物などの鉱物資源が多孔質粒子として使用できる。また、好適な多孔質粒子としては、モンモリロナイトおよびゼオライト、カオリンなどの鉱物資源があげられ、これらのうちいずれかを少なくとも含有するものを用いることが好ましい。さらに本発明の微生物製剤は少なくとも硫黄細菌を担持していることを特徴とする。この硫黄細菌は、後述するように菌体の大きさが比較的小さいため、このような比較的粒子サイズが小さい多孔質粒子に好適に選択的に担持される点でもこの構成とすることが優れている。   In the microorganism preparation of the present invention, a carrier mainly composed of porous particles is used. The porous particle is a particle having many pores in the particle. For example, mineral resources such as silicate minerals can be used as the porous particles. Moreover, examples of suitable porous particles include montmorillonite, mineral resources such as zeolite and kaolin, and it is preferable to use those containing at least one of these. Furthermore, the microorganism preparation of the present invention is characterized by carrying at least sulfur bacteria. Since this sulfur bacterium has a relatively small cell size as will be described later, this sulfur bacterium is also excellent in this configuration in that it is suitably and selectively supported on such porous particles having a relatively small particle size. ing.

本発明の多孔質粒子は中性のものである。ここで中性の多孔質粒子とは、多孔質粒子を水に混合したときのpHを測定したとき、pHが中性域となるものである。多孔質粒子が中性であることを確認するにあたっては、水100gに多孔質粒子10gを撹拌混合した後のpHを求めればよい。このときのpHが、5.5〜8.5であることが好ましく、6〜8であることがより好ましい。中性の多孔質粒子を用いることで、その多孔質粒子を用いた担体に担持される硫黄細菌の定着性が向上する。また、この中性の多孔質粒子を用いた微生物製剤を使用環境に散布したとき、当該環境のpHを変化させるおそれが少なくなるため、広範囲に使用できる微生物製剤を得ることができる。   The porous particles of the present invention are neutral. Here, the neutral porous particles are those in which the pH is in a neutral range when the pH when the porous particles are mixed with water is measured. In confirming that the porous particles are neutral, the pH after stirring and mixing 10 g of the porous particles with 100 g of water may be obtained. The pH at this time is preferably 5.5 to 8.5, and more preferably 6 to 8. By using neutral porous particles, the fixability of sulfur bacteria supported on a carrier using the porous particles is improved. In addition, when the microbial preparation using the neutral porous particles is dispersed in the use environment, the possibility of changing the pH of the environment is reduced, so that a microbial preparation that can be used in a wide range can be obtained.

本発明の多孔質粒子には、粒子サイズ50μm以下のものを主として用いる。この粒子サイズとは、その目開きを有する篩を通過するサイズから求められる。たとえば、目開き53μmである270メッシュの篩を通過する多孔質粒子の最大粒子サイズは53μmであり、当該目開き53μmである270メッシュの篩を用いて篩分けされた多孔質粒子のサイズは53μm以下である。本発明の多孔質粒子には、目開き45μmの325メッシュにより篩分けできる、45μm以下の多孔質粒子を主としたもの用いることがより好ましい。このような粒子サイズの多孔質粒子を主とする担体として使用することで、得られる微生物製剤の分散性が優れたものとなる。本発明の微生物製剤を好適に使用できる対象として池や海のような水系の場所がある。このような水系の場所でも、本発明の粉体状の微生物製剤を散布するだけで、わずかな水流しかなくても、十分に分散する。また、このような粒子サイズの多孔質粒子は、沈降速度も低いため、水中の深さ方向にも徐散される。   As the porous particles of the present invention, those having a particle size of 50 μm or less are mainly used. This particle size is determined from the size passing through a sieve having the openings. For example, the maximum particle size of the porous particles passing through a 270 mesh sieve having an opening of 53 μm is 53 μm, and the size of the porous particles sieved using the 270 mesh sieve having an opening of 53 μm is 53 μm. It is as follows. As the porous particles of the present invention, it is more preferable to use mainly porous particles of 45 μm or less that can be sieved with a 325 mesh having an opening of 45 μm. By using porous particles having such a particle size as a main carrier, the dispersibility of the resulting microbial preparation is excellent. Water-based places such as ponds and seas are suitable for the use of the microorganism preparation of the present invention. Even in such a water-based place, the powdery microbial preparation of the present invention is simply sprayed, and even if there is only a small water flow, it can be sufficiently dispersed. In addition, since the porous particles having such a particle size have a low sedimentation rate, they are gradually dispersed in the depth direction in water.

本発明の多孔質粒子は前述したように比較的小さいサイズの粒子を主とする。この担体中における多孔質粒子の量は、70容量%以上であり、より好ましくは80重量%以上、特に好ましくは90重量%以上である。担体として用いられる多孔質粒子には、一部、粒子サイズが大きいものが含まれていても、前述した要件を満たせば分散性等は十分に発揮される。   As described above, the porous particles of the present invention are mainly particles having a relatively small size. The amount of the porous particles in the carrier is 70% by volume or more, more preferably 80% by weight or more, and particularly preferably 90% by weight or more. Even if the porous particles used as the carrier partially include those having a large particle size, the dispersibility and the like are sufficiently exhibited if the above-described requirements are satisfied.

本発明の粉体状微生物製剤は硫黄細菌を担持させたものである。ここで、硫黄細菌とは、硫黄及び硫黄化合物を酸化または還元することによってエネルギーを得ている化学合成独立栄養細菌である。主に硫化水素を酸化して硫黄とし、更に硫酸にまで酸化することのできる細菌群の総称である。このような硫黄細菌の例として硫黄酸化細菌ともいわれ、色素の有無によって無色硫黄細菌及び有色硫黄細菌に大別される細菌群があげられる。無色硫黄細菌は、好気性で糸状体を形成するものとしてベギアトア(Beggiatoa)、チオトリックス(Thiothrix)、チオプロカ(Thioploca)などがあり、かん(桿)状を呈するものにチオバシラス(Thiobacillus)、アクロマチウム(Achromatium)、アシドチオバチルス(Acidithiobacillus)などの属が知られている。有色硫黄細菌は、嫌気性で紅色を呈するかん状のクロマチウム(Chromatium)、チオカプサ(Thiocapsa)、緑でかん状のクロロビウム(Chlorobium)などの属がある。有色硫黄細菌は、光合成色素(バクテリオクロロフィル)を含み、光合成を行うことから、光合成細菌ともいわれている。本発明においては、これらのいずれの硫黄細菌を用いても良く前述したような硫黄細菌群より選択される少なくとも1以上の硫黄細菌を用いることが好ましい。   The powdery microbial preparation of the present invention carries sulfur bacteria. Here, the sulfur bacterium is a chemically synthesized autotrophic bacterium that obtains energy by oxidizing or reducing sulfur and a sulfur compound. It is a general term for a group of bacteria that can mainly oxidize hydrogen sulfide to sulfur and further oxidize to sulfuric acid. Examples of such sulfur bacteria are also referred to as sulfur-oxidizing bacteria, and include bacterial groups roughly classified into colorless sulfur bacteria and colored sulfur bacteria depending on the presence or absence of pigments. Colorless sulfur bacteria include aerobic and filamentous forms such as Beggiatoa, Thiothrix, and Thioploca. Thybacillus and achromati A genus such as Achromatium and Acidthiothiobacillus is known. Colored sulfur bacteria include anaerobic and red-colored canine chromates (Chromatium), thiocapsa, green and cannabis (Chlorobium). The colored sulfur bacterium contains a photosynthetic pigment (bacteriochlorophyll) and performs photosynthesis, so it is also called a photosynthetic bacterium. In the present invention, any of these sulfur bacteria may be used, and at least one sulfur bacterium selected from the group of sulfur bacteria described above is preferably used.

本発明においては、前述したように粒子サイズが小さい多孔質粒子を主としたものを用いる為、必然的に当該多孔質粒子の孔も小さいものとなるが、本発明に用いる硫黄細菌は、その大きさが0.5〜10μm程度の幅の糸状菌などが多く、本発明に用いる多孔質粒子に選択的に担持され増殖しやすい菌である。この組み合わせは、他の菌による置換や、硫黄細菌の流失などが生じにくい点からも優れている。   In the present invention, as described above, since mainly the porous particles having a small particle size are used, the pores of the porous particles are inevitably small. There are many filamentous fungi having a size of about 0.5 to 10 μm in width, and the like, which are selectively carried on the porous particles used in the present invention and are easy to grow. This combination is also excellent in that it is unlikely to cause substitution with other bacteria or loss of sulfur bacteria.

本発明の微生物製剤には、さらに好気性細菌および/または通性嫌気性細菌を混合することができる。好気性細菌とは、酸素に基づく代謝機構を備えて生育に酸素を必要とする菌であり、通性嫌気性細菌とは、酸素の有無に関わらず生育する菌であり、これらの菌は特に有機物の浄化に寄与する。本発明においては、これらの菌として、カビ、酢酸菌、乳酸菌、酵母等の菌を担持などの態様で混合させておくことが好ましい。また、直接担体である多孔質粒子に担持させずとも各種菌の乾燥粉体を混合してもよい。   Aerobic bacteria and / or facultative anaerobic bacteria can be further mixed in the microorganism preparation of the present invention. Aerobic bacteria are bacteria that have an oxygen-based metabolic mechanism and require oxygen for growth, and facultative anaerobic bacteria are bacteria that grow with or without oxygen. Contributes to the purification of organic matter. In the present invention, it is preferable to mix fungi such as fungi, acetic acid bacteria, lactic acid bacteria, and yeasts as these bacteria in a supported manner. Moreover, you may mix the dry powder of various microbes, without making it carry | support to the porous particle which is a support | carrier directly.

本発明の微生物製剤は、袋に封入して用いられても良い。特に、水流が大きい場所では粉体状微生物製剤が分散されすぎて一定期間経過後に効果が低下しやすくなる場合があるが、このような袋状微生物製剤とすることで、使用環境に長期間保持できる。さらに袋に封入して水系にて使用すると、本発明の多孔質粒子が粘度様に固化してその袋内で塊状となり、さらにこの塊状体から、硫黄細菌が除散されるため、流失等することなく長期間安定した効果を奏する。   The microorganism preparation of the present invention may be used by being enclosed in a bag. Especially in places with a large water flow, the powdered microbial preparation may be excessively dispersed and the effect may be reduced after a certain period of time. it can. Furthermore, when encapsulated in a bag and used in an aqueous system, the porous particles of the present invention solidify like a viscosity and become agglomerated in the bag, and further, sulfur bacteria are dissipated from the agglomerated material, so that it is washed away. There is a long-term stable effect.

袋に封入するとき、本発明の粉体状微生物製剤に加え、白砂および珪砂を混合して封入することが好ましい。これは、沈降性の観点からと、担持される硫黄細菌として光合成細菌が含まれていることが好ましく、その光合成をおこないやすいようにする点から混合されるものである。一定の光透過性や分散性を有する白砂や珪砂を混合しておくことで、袋状微生物製剤の内部にも光が到達しやすくなるため、袋状微生物製剤全体としての浄化機能等を奏しやすくなる。   When encapsulating in a bag, it is preferable to mix and encapsulate white sand and quartz sand in addition to the powdery microorganism preparation of the present invention. From the standpoint of sedimentation, it is preferable that a photosynthetic bacterium is contained as a supported sulfur bacterium, and is mixed from the viewpoint of facilitating the photosynthesis. By mixing white sand or silica sand with a certain light transmittance and dispersibility, light easily reaches the inside of the bag-shaped microbial preparation, so it is easy to perform the purification function of the bag-shaped microbial preparation as a whole. Become.

袋状微生物製剤とする時、その袋には、植物由来成分の樹脂を用いるポリ乳酸のような生分解性不織布を用いることが好ましい。袋として生分解性不織布を用いることで、袋自体による環境汚染のおそれがなくなるため、この袋状微生物製剤を利用しやすくなる。このような生分解性不織布製の袋を用いたものは、特に海のように広くて回収が困難な環境で使用する際に適している。一方、非生分解性の織布(例えばポリエステルのような化学樹脂製の織布)や不織布による袋を用いることもでき、このような非生分解性のものは、池や水田のように散布位置を特定し回収して再利用しやすい場所での使用に適している。   When a bag-like microbial preparation is used, it is preferable to use a biodegradable nonwoven fabric such as polylactic acid using a plant-derived resin. By using a biodegradable non-woven fabric as the bag, there is no risk of environmental pollution due to the bag itself, and this bag-shaped microbial preparation can be easily used. Such a biodegradable non-woven bag is particularly suitable for use in an environment that is wide and difficult to recover, such as the sea. On the other hand, non-biodegradable woven fabric (for example, a woven fabric made of a chemical resin such as polyester) or a bag made of non-woven fabric can be used. It is suitable for use in locations where it is easy to identify and retrieve the location and reuse it.

袋状微生物製剤とする時、粉体状微生物製剤と、白砂と珪砂との混合比率は、その袋状微生物製剤の使用環境に併せて適宜設定することができる。例えば、多孔質粒子100重量部に対して、白砂5〜30重量部、珪砂5〜20重量部の混合比率とすることができる。   When the bag-shaped microbial preparation is used, the mixing ratio of the powdered microbial preparation and the white sand and quartz sand can be appropriately set according to the use environment of the bag-shaped microbial preparation. For example, the mixing ratio can be 5 to 30 parts by weight of white sand and 5 to 20 parts by weight of silica sand with respect to 100 parts by weight of the porous particles.

本発明の粉体状微生物製剤および袋状微生物製剤は、水の浄化、ヘドロの分解、土壌改良、消臭およびプランクトン発生抑制の少なくとも1以上の環境浄化方法に用いることができる。すなわち、水の浄化やヘドロの分解、土壌改良、消臭、プランクトンの発生抑制に利用することができるため、各目的に使用した方法として達成することができる。より具体的には、水の浄化方法に用いる場合、浄化対象となる水として例えば浄化槽や、海、池、沼、小川、養殖場、水槽等があげられる。これらに本発明の微生物製剤を静置したり、単に水面に散布する等の方法で浄化することができる。例えば、水槽に、本発明の袋状微生物製剤を入れておくとその水槽の水が汚染されにくく、透明度の高い水質管理を行うことができる。   The powdery microorganism preparation and the bag-like microorganism preparation of the present invention can be used in at least one environmental purification method of water purification, sludge decomposition, soil improvement, deodorization, and plankton generation suppression. That is, since it can be used for water purification, sludge decomposition, soil improvement, deodorization, and plankton generation suppression, it can be achieved as a method used for each purpose. More specifically, when used in a water purification method, examples of water to be purified include septic tanks, seas, ponds, swamps, streams, farms, and aquariums. These can be purified by a method such as leaving the microbial preparation of the present invention stationary or simply spraying it on the water surface. For example, when the bag-shaped microbial preparation of the present invention is placed in a water tank, the water in the water tank is hardly contaminated, and water quality management with high transparency can be performed.

また、本発明の微生物製剤を用いたヘドロの分解方法として達成することもできる。ヘドロは、有機物を多量に含有する底質中で有機物を過剰に生物分解し、嫌気性状態になっているもので、硫化水素などの硫化物が発生し、好気性細菌や通性嫌気性細菌が生息しにくくなったものである。特に硫化水素の発生が顕著に確認されるヘドロを硫化水素ヘドロと呼ぶ場合がある。このようなヘドロは、原生動物等による有機物の分解が困難となり、浄化されにくくなるが、本発明の粉体状微生物製剤を混合や、散布、袋状製剤を周辺に静置しておくことで、これらのヘドロを分解し、本来の底質に戻すことができる。   Moreover, it can also be achieved as a method for decomposing sludge using the microorganism preparation of the present invention. Sludge is an anaerobic state in which organic matter is excessively biodegraded in sediment containing a large amount of organic matter, and sulfides such as hydrogen sulfide are generated, resulting in aerobic bacteria and facultative anaerobic bacteria. Is difficult to live. In particular, sludge in which the generation of hydrogen sulfide is remarkably confirmed may be referred to as hydrogen sulfide sludge. Such sludge is difficult to decompose organic matter by protozoa and difficult to purify, but by mixing and spraying the powdered microbial preparation of the present invention, the bag-shaped preparation can be left in the vicinity. These sludge can be decomposed and returned to the original sediment.

また、本発明の微生物製剤を用いた土壌改良方法としても達成することができる。土壌改良を行うには、本発明の微生物製剤を混合や散布することで、土壌の電気伝導度を正常化したりし、その土壌を改良することができる。この改良された土壌は、各種植物が生育しやすいものとなる。具体的には、野菜や花、芝生、植木、樹木、果樹等に用いることができる。   It can also be achieved as a soil improvement method using the microorganism preparation of the present invention. In order to improve the soil, it is possible to normalize the electrical conductivity of the soil and improve the soil by mixing and spraying the microbial preparation of the present invention. This improved soil makes it easy for various plants to grow. Specifically, it can be used for vegetables, flowers, lawn, planting trees, trees, fruit trees and the like.

また、本発明の微生物製剤を用いた消臭方法としても達成することができる。この場合も、消臭したい生ごみ、排水溝、汲み取り式トイレなどの対象に、散布したりすることで消臭効果を発揮する。   It can also be achieved as a deodorizing method using the microorganism preparation of the present invention. In this case as well, the deodorizing effect can be achieved by spraying it on objects such as garbage, drains, and flush toilets.

また、本発明の微生物製剤を用いたプランクトンの発生抑制方法としても達成することができる。すなわち、海・湖沼・河川などの水域が、貧栄養状態から富栄養に伴うプランクトン等の異常発生の抑制等にもちいることができ、これにより赤潮やアオコの改善や予防を行うことができる。   It can also be achieved as a plankton generation suppression method using the microorganism preparation of the present invention. In other words, water areas such as seas, lakes, and rivers can be used to suppress the occurrence of abnormalities such as plankton accompanying eutrophication from oligotrophic conditions, thereby improving and preventing red tides and sea cucumbers.

以下、実施例により本発明を更に詳細に説明するが、本発明は、その要旨を変更しない限り以下の実施例に限定されるものではない。   EXAMPLES Hereinafter, although an Example demonstrates this invention further in detail, this invention is not limited to a following example, unless the summary is changed.

「微生物製剤の調製」
「担体」
中性の多孔質粒子であるモンモリロナイトを豊富に含む風化生成物層の土壌を、325メッシュ(目開き45μm)の金網篩で、篩わけし、粒子サイズ45μm以下の粒子を得た。この粒子を本発明の微生物製剤の担体とした。
「微生物」
(培養液a.硫黄細菌の培養液)
本発明の微生物製剤に担持させる微生物として、硫黄酸化菌属であるアシドチオバチルス属が優占的に培養される公知の培養液を用いて培養し、硫黄細菌の培養液aを調製した。
(培養液b.通性嫌気性細菌の培養液)
本発明の微生物製剤に担持させる微生物群として、乳酸菌および酵母が優占的に培養される公知の培養液を用いて、通性嫌気性細菌の培養液bを調製した。
「担持方法」
培養液aの培養液5重量部と、培養液bの培養液5重量部と、水90重量部を混合し培養液希釈液を製造した。この培養液希釈液100重量部を、前述の担体2000重量部に散布し、常温で自然乾燥することで担体に微生物を担持させた粉体状微生物製剤(B)を得た。
"Preparation of microbial preparations"
"Carrier"
The soil of the weathered product layer rich in montmorillonite, which is neutral porous particles, was sieved with a 325 mesh (mesh opening: 45 μm) wire mesh sieve to obtain particles having a particle size of 45 μm or less. These particles were used as a carrier for the microorganism preparation of the present invention.
"Microorganisms"
(Culture solution a. Culture solution of sulfur bacteria)
As a microorganism to be supported on the microorganism preparation of the present invention, a culture solution a of sulfur bacteria was prepared by culturing using a known culture solution in which Acidthiobacillus genus, a sulfur-oxidizing genus, is preferentially cultured.
(Culture solution b. Culture solution of facultative anaerobic bacteria)
A culture solution b of facultative anaerobic bacteria was prepared using a known culture solution in which lactic acid bacteria and yeast are preferentially cultured as a group of microorganisms to be carried on the microorganism preparation of the present invention.
"Supporting method"
A culture solution dilution was prepared by mixing 5 parts by weight of the culture solution of the culture solution a, 5 parts by weight of the culture solution of the culture solution b, and 90 parts by weight of water. 100 parts by weight of the culture broth diluted solution was sprayed on 2000 parts by weight of the above-mentioned carrier and naturally dried at room temperature to obtain a powdery microbial preparation (B) in which the carrier was loaded with microorganisms.

「パック(袋状微生物製剤)」
袋状微生物製剤(パック製剤)とするために、目付70g/m2のポリ乳酸製不織布袋を使用した。この袋に、粉体状微税物製剤(B)85重量部に対して珪砂及び白砂(珪砂:白砂=1:1(重量比))の混合物15重量部を混合したものを1kg封入することで袋状微生物製剤(A)を得た。なお、以下の試験例において、この袋状微生物製剤(A)を主として使用するが、適宜、その内容物である粉体状微生物製剤(B)も使用した。
"Pack (bag-like microorganism preparation)"
In order to obtain a bag-like microorganism preparation (pack preparation), a polylactic acid non-woven bag having a basis weight of 70 g / m 2 was used. In this bag, 1 kg of a mixture of 15 parts by weight of a mixture of silica sand and white sand (silica sand: white sand = 1: 1 (weight ratio)) to 85 parts by weight of the powdered fine tax preparation (B) is sealed. A bag-like microorganism preparation (A) was obtained. In the following test examples, the bag-shaped microbial preparation (A) was mainly used, but the powdered microbial preparation (B) as the contents was also used as appropriate.

「測定方法」
[硫化物]:底質調査方法(昭和63年9月8日付け環水管第127号)II.17に則って測定した。
[COD]:JIS K0102(2008)17に則って測定した。
[全窒素(T−N)]測定法(N1):底質調査方法(昭和63年9月8日付け環水管第127号)II.18に則って測定した。
[全窒素(T−N)]測定法(N2):JIS K0102(2008)45.4に則って測定した。
[全リン(T―P)]測定法(P1):底質調査方法(昭和63年9月8日付け環水管第127号)II.19に則って測定した。
[全リン(T―P)]測定法(P2):JIS K0102(2008)46.1.1に則って測定した。
[強熱減量]:底質調査方法(昭和63年9月8日付け環水管第127号)II.4に則って測定した。
[透視度]:JIS K0102(2008)9に則って測定した。
[臭気]:カルモア社製“カルモアシグマ SK−210”を用いて臭気のシグマ値を測定した。
[EC]:サトテック社製 “防水導電率系計 PCD−431”を用いて土壌のEC値を測定した。
"Measuring method"
[Sulphides]: Bottom sediment investigation method (annular water tube No. 127 dated September 8, 1988) II. Measured according to 17.
[COD]: Measured according to JIS K0102 (2008) 17.
[Total nitrogen (TN)] Measurement method (N1): Bottom sediment investigation method (annual water tube No. 127 dated September 8, 1988) II. Measured according to 18.
[Total nitrogen (TN)] Measurement method (N2): Measured according to JIS K0102 (2008) 45.4.
[Total phosphorus (TP)] Measurement method (P1): Bottom sediment investigation method (annular water tube No. 127 dated September 8, 1988) II. Measured according to 19.
[Total phosphorus (TP)] Measurement method (P2): Measured according to JIS K0102 (2008) 46.1.1.
[Loss on ignition]: Bottom sediment investigation method (annular water tube No. 127 dated September 8, 1988) II. Measured according to 4.
[Transparency]: Measured according to JIS K0102 (2008) 9.
[Odor]: The sigma value of odor was measured using “Calmore Sigma SK-210” manufactured by Calmore.
[EC]: The EC value of the soil was measured using a “waterproof conductivity meter PCD-431” manufactured by Satotech.

[試験例1:水の浄化試験]
[試験環境]
場所:福岡県内の貯水池(水量:約12万トン)
試験開始前の7月頃、この貯水池には、アオコが発生し、透明度の悪化・悪臭の発生、既設の砂ろ過装置の閉塞が問題となっていた。
[Test Example 1: Water purification test]
[Test environment]
Location: Reservoir in Fukuoka Prefecture (Water volume: about 120,000 tons)
Around July before the start of the test, water reservoirs were generated in this reservoir, resulting in problems of deterioration of transparency, generation of bad odor, and blockage of existing sand filtration devices.

[試験方法]
使用製剤と使用量:袋状微生物製剤(A)50袋(50kg)、粉状微生物製剤(B)30kg
散布方法:池に袋状微生物製剤(A)を均等に配置した(約400m2に1袋)。また、その後さらに池の中心付近を航行するボートスクリューによる水流を利用して粉体状微生物製剤(B)30kgを池全体に拡散させた。なお、試験開始時のこの池のpHは、8.79であった。
試験例1の分析結果を表1に示す。
[Test method]
Formulations and amounts used: 50 bag sachets (A) (50 kg), 30 kg powder microbials (B)
Application method: The bag-shaped microbial preparation (A) was evenly arranged in the pond (one bag at about 400 m 2 ). Further, 30 kg of the powdered microbial preparation (B) was diffused throughout the pond using a water flow generated by a boat screw that sailed near the center of the pond. The pH of this pond at the start of the test was 8.79.
The analysis results of Test Example 1 are shown in Table 1.

Figure 2015231351
Figure 2015231351

本発明の微生物製剤を散布し水質を浄化させることで、硫化物濃度やCODが低減することを確認することができた。さらに、この池のアオコを抑制し、透視度が向上し、臭気も改善された。また、この池に取り付けられていたろ過装置への負荷も軽減された。   It was confirmed that the sulfide concentration and COD were reduced by spraying the microorganism preparation of the present invention to purify the water quality. In addition, the water in the pond was suppressed, the transparency increased, and the odor improved. The load on the filtration device attached to this pond was also reduced.

[試験例2:ヘドロの分解試験]
[試験環境]
場所:長崎県島原市 有明海アサリ漁場(砂浜・河口)
試験開始前、この漁場はアオサが大量に打ち上げられ、それが腐敗堆積しヘドロ化して悪臭がしており、硫化物発生のためにアサリが収穫できなくなっていた。
[Test Example 2: Degradation test of sludge]
[Test environment]
Location: Ariake Sea clam fishing ground (sand beach, river mouth), Shimabara City, Nagasaki Prefecture
Before the start of the test, a large amount of sea bream was launched at this fishing ground, which decayed and became muddy and had a bad odor, and the clams could not be harvested due to the occurrence of sulfides.

[試験内容]
(砂浜):アサリ漁場の砂浜海岸線約500mの区画に、20m毎に杭を打ち袋状微生物製剤(A)を1袋(内容量1kg)ずつ網袋に入れて計25袋(25kg)を設置した。また、設置後、粉体状微生物製剤(B)4本(4kg)を砂浜に散布した。
試験例2の砂浜の分析結果を表2に示す。
(河口):当該アサリ漁場に流れ込む川の上流に袋状微生物製剤(A)を4袋(4kg))設置し、粉体状微生物製剤(B)を1kg散布した。
試験例2の加工の分析結果を表3に示す。
[contents of the test]
(Sand beach): In the section of the sandy shoreline of the clam fishing ground about 500m, piles are piled every 20m and a bag-like microbial preparation (A) is put into a net bag (1kg content), and a total of 25 bags (25kg) are installed. did. Moreover, after installation, four powdery microbial preparations (B) (4 kg) were sprayed on the sandy beach.
The analysis results of the sandy beach of Test Example 2 are shown in Table 2.
(Kawaguchi): Four bags (4 kg) of the bag-like microbial preparation (A) were installed upstream of the river flowing into the clam fishing ground, and 1 kg of the powder microbial preparation (B) was sprayed.
Table 3 shows the analysis results of the processing of Test Example 2.

Figure 2015231351
Figure 2015231351

Figure 2015231351
Figure 2015231351

経過:腐敗臭がしなくなり、ヘドロで埋まっていた浜の砂地がはっきりと見えるようになり元の砂浜に戻った。また、アサリの稚貝を放流できるほどにまで回復した。   Progress: The smell of rotting disappeared, and the sandy beach that had been buried in sludge became clearly visible and returned to the original sandy beach. In addition, it recovered to the point where the clams were released.

[試験例3:底質改善]
[試験内容]
場所:福岡県内の競艇場 約8万m2
競艇場の競走プールの流入水には、その上流にある水田の肥料や農薬などが含まれており、窒素分が非常に多い状態で、アオコの発生がひどい状態だった。また、そのアオコを一時的に抑制するために長年防錆剤を散布してきており、底質が非常に悪化していた。
散布量:袋状微生物製剤(A)16袋(16kg)、粉体状微生物製剤(B)16kg
競争プールに袋状微生物製剤(A)を均等に配置した。また、粉体状微生物製剤(B)を全体に散布した。
試験開始時期:4月
試験例3の分析結果を表4に示す。
[Test Example 3: Bottom sediment improvement]
[contents of the test]
Location: Approximately 80,000m 2
The inflow water from the racetrack on the racetrack contained fertilizers and pesticides in the paddy fields upstream of it, and the amount of nitrogen was very high, and the occurrence of blue sea bream was terrible. Moreover, rust preventives have been sprayed for many years in order to temporarily suppress the sea cucumber, and the bottom quality has been greatly deteriorated.
Application amount: 16 bags of microbial preparation (A) (16 kg), 16 kg of powdered microbial preparation (B)
The bag-like microbial preparation (A) was evenly arranged in the competitive pool. Moreover, the powdery microbial preparation (B) was sprayed on the whole.
Test start time: April Table 4 shows the analysis results of Test Example 3.

Figure 2015231351
Figure 2015231351

経緯:アオコの養分となる底質中の窒素やリンを確実に減少させており、一定のアオコ改善効果がみられた。 Background: Nitrogen and phosphorus in the bottom sediments, which are the nutrients for the sea cucumber, were reliably reduced, and a certain level of sea cucumber improvement was observed.

[試験例4:水質・底質改善]
[試験内容]
場所:福岡県内の城の濠 約1500m2
散布製剤と使用量:袋状微生物製剤(A)3袋(3kg)、粉体状微生物製剤(B)3kg
濠に袋状微生物製剤(A)を均等に配置した。また、粉体状微生物製剤(B)を全体に散布した。
試験開始時期:12月
試験例4の分析結果を表5に示す。
[Test Example 4: Improvement of water and bottom quality]
[contents of the test]
Location: Castle castle in Fukuoka Prefecture 1500m 2
Spray formulation and amount used: bag-shaped microbial preparation (A) 3 bags (3 kg), powdered microbial preparation (B) 3 kg
The bag-like microbial preparation (A) was evenly arranged on the basket. Moreover, the powdery microbial preparation (B) was sprayed on the whole.
Test start time: December Table 5 shows the analysis results of Test Example 4.

Figure 2015231351
Figure 2015231351

経過:表5に示すように測定項目に変化があった。加えて、濠の水の透明度向上及び底質改善(硫化物の分解)と、それらによるハスの再生が確認された。 Progress: As shown in Table 5, the measurement items changed. In addition, the improvement of transparency and bottom sediment (decomposition of sulfide) and the regeneration of lotus were confirmed.

[試験例5:臭気の改善]
[試験内容]
場所:佐賀県内の有明ノリ乾燥工場
使用製剤と使用量:粉体状微生物製剤(B)1kg
散布方法:工場排水の排水槽(約400t)内、及び工場〜排水槽間の水路上流に散布した。
試験開始時期:12月
試験内容:ノリ屑が排水槽内に堆積し悪臭がひどく、最終的に川へ排水した際にノリの色素のために水がピンク色になってしまうのを改善する目的。水産ノリ乾燥工場の排水槽(A)にはなにも散布せず、水産ノリ乾燥工場の排水槽(B)に上記のとおり微生物製剤を散布した。
試験例5の分析結果を表6に示す。
[Test Example 5: Improvement of odor]
[contents of the test]
Location: Ariake Nori Drying Plant in Saga Prefecture
Formulation and amount used: 1 kg powdered microbial formulation (B)
Spraying method: sprayed in the drainage tank (about 400 t) of factory wastewater and upstream of the water channel between the factory and the drainage tank.
Test start time: December Test content: The purpose of improving the waste water that is accumulated in the drainage tank and has a bad odor, and finally the water turns pink due to the pigment of the paste when it drains into the river. . Nothing was sprayed on the drainage tank (A) of the fishery drying factory, and the microbial preparation was sprayed on the drainage tank (B) of the fishery drying factory as described above.
The analysis results of Test Example 5 are shown in Table 6.

Figure 2015231351
Figure 2015231351

経過:本発明の微生物製剤を散布することで排水槽の臭気が抑制された。また、排水のピンクの着色も改善された。なお、上記の臭気シグマ値が高いほど臭気が高く、このシグマ値は相対的な値として確認するものである。試験時、外気では333〜340を示す状態であり、対照槽である水槽(A)は微生物製剤の散布を行わなかったため1079まで上昇したが、微生物製剤の散布を行った水槽(B)は、630までしか上昇しなかった。 Progress: The odor of the drainage tank was suppressed by spraying the microorganism preparation of the present invention. In addition, the pink color of the drainage was improved. The higher the odor sigma value, the higher the odor, and this sigma value is confirmed as a relative value. At the time of the test, the outside air is in a state showing 333 to 340, and the water tank (A) which is the control tank rose to 1079 because the microbial preparation was not sprayed, but the water tank (B) which was sprayed with the microbial preparation was It rose only to 630.

[試験例6:土壌の改善]
場所:農作物用ハウスの土壌 (作付け用面積:8m×50m)
使用製剤と使用量:粉体状微生物製剤(B)を、散布量が5g/m2となるように散布した。
[Test Example 6: Improvement of soil]
Place: Soil of crop house (Agricultural area: 8m x 50m)
Use formulation and use amount: The powdery microorganism preparation (B) was sprayed so that the spray amount was 5 g / m 2 .

本発明の粉体状微生物製剤を散布する前の肥料ECの値1800μS/cmであり作付に適さない高い値であったが、散布後700μS/cmまで低下した。   The value of the fertilizer EC before spraying the powdered microorganism preparation of the present invention was 1800 μS / cm, which was a high value unsuitable for cropping, but decreased to 700 μS / cm after spraying.

本発明の微生物製剤は、水の浄化やヘドロの分解、土壌改良、消臭、プランクトンの発生抑制等に用いることができ、産業上利用可能である。   The microorganism preparation of the present invention can be used for purification of water, decomposition of sludge, soil improvement, deodorization, suppression of plankton generation, and the like, and is industrially applicable.

すなわち、本発明は、以下の発明に係るものである。
<1> 粒子サイズ50μm以下の中性の多孔質粒子として、モンモリロナイトおよびゼオライト、カオリンからなる群から選択される少なくとも1種以上である多孔質粒子を70容量%以上含む担体に、硫黄細菌を優占的に培養した培養液を接触させ乾燥することで硫黄細菌を優占的に担持させた粉体状微生物製剤。
<2> さらに好気性細菌および/または通性嫌気性細菌を混合させた前記<1>記載の粉体状微生物製剤。
> 前記<1>または<2>に記載の粉体状微生物製剤に、珪砂及び白砂を混合し、通水性を有する袋に封入した袋状微生物製剤。
> 封入に用いられる前記袋が生分解性不織布製である前記<>記載の袋状微生物製剤。
> 前記<1>〜<>のいずれかに記載の粉体状微生物製剤および/または袋状微生物製剤を用いた、水の浄化、ヘドロの分解、土壌改良、消臭およびプランクトン発生抑制から選択される少なくとも1以上の環境浄化方法。
That is, the present invention relates to the following inventions.
<1> As a neutral porous particle having a particle size of 50 μm or less, a sulfur bacterium is superior to a carrier containing 70% by volume or more of at least one kind of porous particle selected from the group consisting of montmorillonite, zeolite, and kaolin. A powdery microbial preparation that preferentially supports sulfur bacteria by contacting and drying a precultured culture .
<2> The powdery microbial preparation according to the above <1>, further mixed with aerobic bacteria and / or facultative anaerobic bacteria.
< 3 > A bag-like microbial preparation in which silica powder and white sand are mixed with the powdered microbial preparation according to <1> or <2> and enclosed in a bag having water permeability.
< 4 > The bag-like microorganism preparation according to < 3 >, wherein the bag used for encapsulation is made of a biodegradable nonwoven fabric.
< 5 > Water purification, sludge decomposition, soil improvement, deodorization, and plankton generation suppression using the powdery microorganism preparation and / or bag-like microorganism preparation according to any one of <1> to < 4 > One or more environmental purification methods selected from.

すなわち、本発明は、以下の発明に係るものである。
<1> 粒子サイズ50μm以下の中性の多孔質粒子として、モンモリロナイトおよびゼオライト、カオリンからなる群から選択される少なくとも1種以上である多孔質粒子を70容量%以上含む担体に、硫黄細菌を優占的に培養した培養液を接触させ乾燥することで硫黄細菌を優占的に担持させた粉体状微生物製剤に、
珪砂及び白砂を混合し、通水性を有する袋に封入した袋状微生物製剤であって、
前記袋状微生物製剤において、前記粉体状微生物製剤100重量部に対して、前記珪砂5〜20重量部と、前記白砂5〜30重量部とを混合して封入したことを特徴とする袋状微生物製剤。
<2> さらに好気性細菌および/または通性嫌気性細菌を混合させた前記<2>記載の袋状微生物製剤
<3> 封入に用いられる前記袋が生分解性不織布製の袋である前記<1>または<2>記載の袋状微生物製剤
<4> 前記<1>乃至<3>のいずれかに記載の袋状微生物製剤を用いた、水の浄化、ヘドロの分解、土壌改良、消臭およびプランクトン発生抑制から選択される少なくとも1以上の環境浄化方法。
That is, the present invention relates to the following inventions.
<1> As a neutral porous particle having a particle size of 50 μm or less, a sulfur bacterium is superior to a carrier containing 70% by volume or more of at least one kind of porous particle selected from the group consisting of montmorillonite, zeolite, and kaolin. To the powdery microbial preparation that preferentially carries sulfur bacteria by contacting and drying the culture solution that has been preferentially cultured ,
A bag-like microbial preparation in which silica sand and white sand are mixed and sealed in a bag having water permeability,
In the bag-like microbial preparation, the bag-like microbial preparation is encapsulated by mixing 5 to 20 parts by weight of the silica sand and 5 to 30 parts by weight of the white sand with respect to 100 parts by weight of the powdered microbial preparation. Microbial preparation.
<2> The bag-like microorganism preparation according to <2>, further mixed with aerobic bacteria and / or facultative anaerobic bacteria.
<3> The bag-like microorganism preparation according to <1> or <2>, wherein the bag used for encapsulation is a biodegradable nonwoven fabric bag.
<4> At least one or more selected from purification of water, decomposition of sludge, soil improvement, deodorization, and suppression of plankton generation using the bag- like microorganism preparation according to any one of <1> to <3> Environmental purification method.

Claims (6)

粒子サイズ50μm以下の中性の多孔質粒子を70容量%以上含む担体に、硫黄細菌を担持させた粉体状微生物製剤。   A powdery microbial preparation in which sulfur bacteria are supported on a carrier containing 70% by volume or more of neutral porous particles having a particle size of 50 μm or less. さらに好気性細菌および/または通性嫌気性細菌を混合させた請求項1記載の粉体状微生物製剤。   The powdery microbial preparation according to claim 1, further comprising aerobic bacteria and / or facultative anaerobic bacteria. 前記多孔質粒子が、モンモリロナイトおよびゼオライト、カオリンからなる群から選択される少なくとも1種以上である請求項1または2に記載の粉体状微生物製剤。   The powdery microorganism preparation according to claim 1 or 2, wherein the porous particles are at least one selected from the group consisting of montmorillonite, zeolite, and kaolin. 請求項1乃至3のいずれかに記載の粉体状微生物製剤に、珪砂及び白砂を混合し、通水性を有する袋に封入した袋状微生物製剤。   A bag-like microbial preparation obtained by mixing silica sand and white sand with the powdered microbial preparation according to any one of claims 1 to 3 and enclosing the mixture in a water-permeable bag. 封入に用いられる前記袋が生分解性不織布製である請求項4記載の袋状微生物製剤。   The bag-like microorganism preparation according to claim 4, wherein the bag used for encapsulation is made of a biodegradable nonwoven fabric. 請求項1乃至5のいずれかに記載の粉体状微生物製剤および/または袋状微生物製剤を用いた、水の浄化、ヘドロの分解、土壌改良、消臭およびプランクトン発生抑制から選択される少なくとも1以上の環境浄化方法。   6. At least one selected from water purification, sludge decomposition, soil improvement, deodorization, and plankton generation suppression using the powdery microorganism preparation and / or the bag-like microorganism preparation according to any one of claims 1 to 5. The above environmental purification method.
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