JP2011031180A - Method of making heavy metal, dioxin, nitrate and agricultural chemical harmless - Google Patents

Method of making heavy metal, dioxin, nitrate and agricultural chemical harmless Download PDF

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JP2011031180A
JP2011031180A JP2009180255A JP2009180255A JP2011031180A JP 2011031180 A JP2011031180 A JP 2011031180A JP 2009180255 A JP2009180255 A JP 2009180255A JP 2009180255 A JP2009180255 A JP 2009180255A JP 2011031180 A JP2011031180 A JP 2011031180A
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tateyama
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Nobuko Suzuki
伸子 鈴木
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SUZUKI FARM KK
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Abstract

<P>PROBLEM TO BE SOLVED: To decompose heavy metals, dioxins, nitrates and agricultural chemicals effectively at low costs to make them harmless. <P>SOLUTION: A method of making the harmful substances harmless comprises mixing soy pulp or rice bran with a group of effective microorganisms comprising alkalophilic Bacillus 'tateyama-turugi' FERM BP-10691, alkalophilic Bacillus 'tateyama-yakusi' FERM BP-10692, halophilic Bacillus 'tateyama-jodo' FERM BP-10693, anaerobic Atopostipes 'tateyama-jojo' FERM BP-10690 and anaerobic and halophilic Clostridium 'tateyama-ryuoh' FERM BP-10694, carrying out primary fermentation at 50-100°C for 24 h to form a bed material, mixing a target material with the bed material, mixing the mixture of the target material and the bed material with the group of the effective microorganisms and carrying out secondary fermentation at 60-80°C for 48-72 h. <P>COPYRIGHT: (C)2011,JPO&INPIT

Description

本発明は、カドミウムを含む重金属、ダイオキシン、硝酸塩及び農薬を無害化する方法に関するものである。   The present invention relates to a method for detoxifying heavy metals containing cadmium, dioxins, nitrates and agricultural chemicals.

すなわち、本発明は、土壌、肥料、水、焼却灰、家畜の糞尿、工場排水、汚泥、下水等に含まれる重金属、ダイオキシン、硝酸塩及び農薬を分解し、無害化する方法に関するものである。   That is, the present invention relates to a method for decomposing and detoxifying heavy metals, dioxins, nitrates and agricultural chemicals contained in soil, fertilizer, water, incinerated ash, livestock manure, industrial wastewater, sludge, sewage and the like.

本出願においては、無害化すべき重金属、ダイオキシン、硝酸塩又は農薬を含む土壌、肥料、水、焼却灰、家畜の糞尿、工場排水、汚泥、下水等を被処理物という。   In the present application, soil, fertilizer, water, incinerated ash, livestock manure, factory wastewater, sludge, sewage, etc. containing heavy metals, dioxins, nitrates or agricultural chemicals to be rendered harmless are referred to as objects to be treated.

本発明者等は、特許第3710424号公報において、重金属、ダイオキシン類及び農薬を分解する方法(以下[従来の方法]という。)を提供している。   In Japanese Patent No. 3710424, the present inventors provide a method for decomposing heavy metals, dioxins and agricultural chemicals (hereinafter referred to as [conventional method]).

従来の方法は、配合株数の割合が好気性菌群55%と嫌気性菌群45%とよりなる有効微生物群を有機廃棄物に混入して40〜200℃の温度にて一次発酵させ、更にこれに配合株数の割合が好気性菌群55%と嫌気性菌群45%とよりなる有効微生物群を混入し、これを被処理物と共に100〜200℃の温度にて二次発酵させることにより、該被処理物に含まれる重金属、ダイオキシン類又は農薬を分解させるようにしたことを特徴とする重金属、ダイオキシン類及び農薬を分解する方法である。 In the conventional method, an effective microorganism group composed of 55% aerobic bacteria group and 45% anaerobic bacteria group is mixed in organic waste, and primary fermentation is performed at a temperature of 40 to 200 ° C. By mixing this with an effective microbial group consisting of 55% aerobic bacteria group and 45% anaerobic bacteria group, and subjecting it to secondary fermentation at a temperature of 100 to 200 ° C. together with the material to be treated. A method for decomposing heavy metals, dioxins and agricultural chemicals, characterized in that heavy metals, dioxins or agricultural chemicals contained in the object to be treated are decomposed.

特許第3710424号公報Japanese Patent No. 3710424

上記従来の方法は、重金属、ダイオキシン類及び農薬を一応分解し得るものではあるが、本発明は、重金属、ダイオキシン、硝酸塩及び農薬を効果的に、かつ、低コストで分解し、無害化する方法を提供しようとしてなされたものである。   Although the above conventional method is capable of decomposing heavy metals, dioxins and agricultural chemicals, the present invention is a method for effectively decomposing and detoxifying heavy metals, dioxins, nitrates and agricultural chemicals at low cost. It was made to offer.

上記課題を解決するために、本発明は、下記の重金属、ダイオキシン、硝酸塩及び農薬を無害化する方法を提供する。   In order to solve the above problems, the present invention provides a method for detoxifying the following heavy metals, dioxins, nitrates and agricultural chemicals.

(1)好アルカリ性のバチルス属タテヤマ剣FERM BP-10691と、好アルカリ性のバチルス属タテヤマ薬師FERM BP−10692と、好塩性のバチルス属タテヤマ浄土FERM BP-10693と、嫌気性菌のアトポスティペス属タテヤマ女汝FERM BP-10690と、嫌気性かつ好塩性のクロストリディウム属タテヤマ竜王FERM BP-10694とよりなる有効微生物群をオカラ又は米ぬかに混入し、50〜100℃の温度にて24時間一次発酵させて床材を形成し、
被処理物を該床材と混合し、
該被処理物と該床材との混合物に、好アルカリ性のバチルス属タテヤマ剣FERM BP-10691と、好アルカリ性のバチルス属タテヤマ薬師FERM BP−10692と、好塩性のバチルス属タテヤマ浄土FERM BP-10693と、嫌気性菌のアトポスティペス属タテヤマ女汝FERM BP-10690と、嫌気性かつ好塩性のクロストリディウム属タテヤマ竜王FERM BP-10694とよりなる有効微生物群を混入し、これを60〜80℃の温度にて48〜72時間二次発酵させることを特徴とする重金属、ダイオキシン、硝酸塩及び農薬を無害化する方法(請求項1)。
(1) The alkalophilic Bacillus genus Tateyama sword FERM BP-10691, the alkalophilic Bacillus genus Tateyama pharmacist FERM BP-10682, the halophilic Bacillus genus Tateyama pure soil FERM BP-10893, and the anaerobic fungus Atopostipes An effective microorganism group consisting of the genus Tateyama female FERM BP-10690 and the anaerobic and halophilic Clostridium genus Tateyama Ryuo FERM BP-10694 is mixed in okara or rice bran at a temperature of 50 to 100 ° C. 24 hours primary fermentation to form flooring,
Mixing the object to be treated with the flooring;
To the mixture of the object to be treated and the flooring, an alkalophilic Bacillus genus sword FERM BP-10691, an alkalophilic Bacillus genus Tateyama pharmacist FERM BP-10692, and a halophilic Bacillus genus Tateyama pure soil FERM BP- An effective microorganism group consisting of 10893, an anaerobic bacterium, Atostipes genus TATEYAMA FERM BP-10690, and anaerobic and halophilic Clostridial genus TATEYAMA Ryuo FERM BP-10694 are mixed. A method of detoxifying heavy metals, dioxins, nitrates and agricultural chemicals, characterized by subjecting to secondary fermentation at a temperature of 60 to 80 ° C. for 48 to 72 hours.

(2)好アルカリ性のバチルス属タテヤマ剣FERM BP-10691と、好アルカリ性のバチルス属タテヤマ薬師FERM BP−10692と、好塩性のバチルス属タテヤマ浄土FERM BP-10693と、嫌気性菌のアトポスティペス属タテヤマ女汝FERM BP-10690と、嫌気性かつ好塩性のクロストリディウム属タテヤマ竜王FERM BP-10694とよりなる有効微生物群をオカラ又は米ぬかに混入し、50〜100℃の温度にて24時間一次発酵させて床材を形成し、
被処理物を該床材と混合し、
該被処理物と該床材との混合物に、好アルカリ性のバチルス属タテヤマ剣FERM BP-10691と、好アルカリ性のバチルス属タテヤマ薬師FERM BP−10692と、好塩性のバチルス属タテヤマ浄土FERM BP-10693と、嫌気性菌のアトポスティペス属タテヤマ女汝FERM BP-10690と、嫌気性かつ好塩性のクロストリディウム属タテヤマ竜王FERM BP-10694とよりなる有効微生物群を混入し、これを加温することなく1〜2ヶ月間自然発酵させることを特徴とする重金属、ダイオキシン、硝酸塩及び農薬を無害化する方法(請求項2)。
(2) The alkalophilic Bacillus Tateyama sword FERM BP-10691, the alkalophilic Bacillus genus Tateyama pharmacist FERM BP-10692, the halophilic Bacillus genus Tateyama pure soil FERM BP-10893, and the anaerobic fungus Atopostipes An effective microorganism group consisting of the genus Tateyama female FERM BP-10690 and the anaerobic and halophilic Clostridium genus Tateyama Ryuo FERM BP-10694 is mixed in okara or rice bran at a temperature of 50 to 100 ° C. 24 hours primary fermentation to form flooring,
Mixing the object to be treated with the flooring;
To the mixture of the object to be treated and the flooring, an alkalophilic Bacillus genus sword FERM BP-10691, an alkalophilic Bacillus genus Tateyama pharmacist FERM BP-10692, and a halophilic Bacillus genus Tateyama pure soil FERM BP- An effective microorganism group consisting of 10893, an anaerobic bacterium, Atostipes genus TATEYAMA FERM BP-10690, and anaerobic and halophilic Clostridial genus TATEYAMA Ryuo FERM BP-10694 are mixed. A method for detoxifying heavy metals, dioxins, nitrates and agricultural chemicals, characterized by natural fermentation for 1 to 2 months without heating (Claim 2).

本発明によれば、土壌、肥料、水、焼却灰、家畜の糞尿、工場排水、汚泥、下水等に含まれる重金属、ダイオキシン、硝酸塩及び農薬を効果的に分解し、無害化することができる。また、有効微生物群とオカラ又は米ぬかとを用いているため、コスト面でも極めて有利であり、通常は廃棄されるオカラ又は米ぬかを有効活用することもできる。更に、被処理物を発酵処理することにより、有用な堆肥を得ることもできる。   According to the present invention, heavy metals, dioxins, nitrates and pesticides contained in soil, fertilizer, water, incinerated ash, livestock manure, industrial wastewater, sludge, sewage, etc. can be effectively decomposed and rendered harmless. Moreover, since the effective microorganism group and okara or rice bran are used, it is extremely advantageous in terms of cost, and the okara or rice bran that is normally discarded can be effectively used. Furthermore, useful compost can also be obtained by carrying out the fermentation process of the to-be-processed object.

図1は、バチルス属(Bacillus sp.)タテヤマ剣とバチルス属(Bacillus sp.)タテヤマ薬師の分子系統樹である。FIG. 1 is a molecular phylogenetic tree of a Bacillus sp. Tateyama sword and a Bacillus sp. Tateyama pharmacist. 図2は、バチルス属(Bacillus sp.)タテヤマ浄土の分子系統樹である。FIG. 2 is a molecular phylogenetic tree of Bacillus sp. 図3は、アトポスティペス属(Atopostipes sp.)タテヤマ女汝の分子系統樹である。FIG. 3 is a molecular phylogenetic tree of Atopostipes sp. Tateyama. 図4は、クロストリディウム属(Clostridium sp.)タテヤマ竜王の分子系統樹である。FIG. 4 is a molecular phylogenetic tree of Clostridium sp.

本発明による重金属、ダイオキシン、硝酸塩及び農薬を無害化する方法は、下記のとおりである。 The method for detoxifying heavy metals, dioxins, nitrates and agricultural chemicals according to the present invention is as follows.

[床材の形成]
まず、好アルカリ性のバチルス属(Bacillus sp.)タテヤマ剣FERM BP-10691と、好アルカリ性のバチルス属(Bacillus sp.)タテヤマ薬師FERM BP−10692と、好塩性のバチルス属(Bacillus
sp.)タテヤマ浄土FERM BP-10693と、嫌気性菌のアトポスティペス属(Atopostipes sp.)タテヤマ女汝FERM BP-10690と、嫌気性かつ好塩性のクロストリディウム属(Clostridium sp.)タテヤマ竜王FERM BP-10694とよりなる有効微生物群をオカラ又は米ぬかに混入し、50〜100℃の温度にて24時間一次発酵させて床材を形成する。
[Formation of flooring]
First, the alkalophilic Bacillus sp. Tateyama sword FERM BP-10691, the alkalophilic Bacillus sp. Tateyama pharmacist FERM BP-10682, and the halophilic Bacillus genus (Bacillus sp.).
sp.) Tateyama Pure Land FERM BP-10893, anaerobic bacteria Atopostipes sp. Tateyama Lady FERM BP-10690, anaerobic and halophilic Clostridium sp. An effective microorganism group consisting of Tateyama Ryuo FERM BP-10694 is mixed in okara or rice bran and subjected to primary fermentation at a temperature of 50 to 100 ° C. for 24 hours to form a flooring material.

一例として、前記有効微生物群2重量部を前記オカラ又は米ぬか35重量部に混入する。 As an example, 2 parts by weight of the effective microorganism group is mixed in 35 parts by weight of Okara or rice bran.

[被処理物を床材と混合]
無害化すべき重金属、ダイオキシン、硝酸塩又は農薬を含む土壌、肥料、水、焼却灰、家畜の糞尿、工場排水、汚泥、下水等の被処理物を該床材と混合する。
[Mixed material to be treated with flooring]
To-be-treated material such as heavy metals, dioxins, nitrates or agricultural chemicals containing soil, fertilizer, water, incinerated ash, livestock manure, industrial wastewater, sludge, sewage, etc. are mixed with the flooring.

一例として、前記被処理物58重量部を床材37重量部と混合する。 As an example, 58 parts by weight of the workpiece is mixed with 37 parts by weight of a flooring material.

[二次発酵]
該被処理物と該床材との混合物に、好アルカリ性のバチルス属(Bacillus sp.)タテヤマ剣FERM BP-10691と、好アルカリ性のバチルス属(Bacillus sp.)タテヤマ薬師FERM BP−10692と、好塩性のバチルス属(Bacillus
sp.)タテヤマ浄土FERM BP-10693と、嫌気性菌のアトポスティペス属(Atopostipes sp.)タテヤマ女汝FERM BP-10690と、嫌気性かつ好塩性のクロストリディウム属(Clostridium sp.)タテヤマ竜王FERM BP-10694とよりなる有効微生物群を混入し、これを60〜80℃の温度にて48〜72時間二次発酵させる。
[Secondary fermentation]
To the mixture of the material to be treated and the flooring, an alkalophilic Bacillus sp. Tateyama sword FERM BP-10691, an alkalophilic Bacillus sp. Tateyama pharmacist FERM BP-10682, Salty Bacillus
sp.) Tateyama Pure Land FERM BP-10893, anaerobic bacteria Atopostipes sp. Tateyama Lady FERM BP-10690, anaerobic and halophilic Clostridium sp. An effective microorganism group consisting of Tateyama Ryuo FERM BP-10694 is mixed and subjected to secondary fermentation at a temperature of 60 to 80 ° C. for 48 to 72 hours.

一例として、該被処理物58重量部と該床材37重量部との混合物95重量部に前記有効微生物群5重量部を混入する。   As an example, 5 parts by weight of the effective microorganism group is mixed in 95 parts by weight of a mixture of 58 parts by weight of the workpiece and 37 parts by weight of the flooring material.

[自然発酵]
上記二次発酵については、該被処理物と該床材との混合物に前記有効微生物群を混入し、これを加温することなく1〜2ヶ月間自然発酵させてもよい。
[Natural fermentation]
About the said secondary fermentation, the said effective microorganism group may be mixed in the mixture of this to-be-processed object and this flooring, and you may ferment naturally for 1 to 2 months, without heating this.

なお、嫌気性菌のアトポスティペス属(Atopostipes sp.)タテヤマ女汝(FERM BP-10690)と、好アルカリ性のバチルス属(Bacillus sp.)タテヤマ剣(FERM BP-10691)と、好アルカリ性のバチルス属(Bacillus sp.)タテヤマ薬師(FERM BP−10692)と、好塩性のバチルス属(Bacillus sp.)タテヤマ浄土(FERM BP-10693)と、嫌気性かつ好塩性のクロストリディウム属(Clostridium sp.)タテヤマ竜王(FERM BP-10694)は、それぞれ独立行政法人産業技術総合研究所特許生物寄託センターに寄託されている。 It should be noted that the anaerobic bacteria Atopostipes sp. Tateyama woman (FERM BP-10690), the alkalophilic Bacillus sp. Genus (Bacillus sp.) Tateyama pharmacist (FERM BP-10692), halophilic Bacillus sp. Tateyama pure soil (FERM BP-10893), anaerobic and halophilic clostridium genus ( Clostridium sp.) Tateyama Ryuo (FERM BP-10694) is deposited at the National Institute of Advanced Industrial Science and Technology Patent Biological Depositary.

好アルカリ性のバチルス属(Bacillus sp.)タテヤマ剣と、好アルカリ性のバチルス属(Bacillus
sp.)タテヤマ薬師と、好塩性のバチルス属(Bacillus sp.)タテヤマ浄土と、嫌気性菌のアトポスティペス属(Atopostipes sp.)タテヤマ女汝と、嫌気性かつ好塩性のクロストリディウム属(Clostridium sp.)タテヤマ竜王とについて、同定を実施した。以下、同定方法及び微生物試験結果を示す。
An alkalophilic Bacillus sp. Tateyama sword and an alkalophilic Bacillus
sp.) Tateyama pharmacist, halophilic Bacillus sp. Tateyama pure soil, anaerobic Atopostipes sp. Tateyama woman, and anaerobic and halophilic Clostridium Identification was conducted with Clostridium sp. Hereinafter, an identification method and a microbial test result are shown.

細菌第一段階試験として、光学顕微鏡U-LH1,000(オリンパス,日本)により、細胞形態、グラム染色性、胞子の有無及び鞭毛による運動性の有無を観察した。NUTRIENT AGAR (OXOID, HAMPSHIRE, ENGLAND)(以下「NT」という。)又はGAM寒天培地(ニッスイ, 東京)(以下「GAM」という。)でのコロニー形態を観察した。カタラーゼ反応、オキシダーゼ反応、グルコースからの酸/ガス産生及びブドウ糖の酸化/発酵(O/F)について試験を行った。
菌学的性状試験結果を表1に示す。
As a bacterial first stage test, cell morphology, Gram staining, presence of spores and motility by flagella were observed with an optical microscope U-LH1,000 (Olympus, Japan). Colony morphology was observed on NUTRIENT AGAR (OXOID, HAMPSHIRE, ENGLAND) (hereinafter referred to as “NT”) or GAM agar medium (Nissui, Tokyo) (hereinafter referred to as “GAM”). Tests were made for catalase reaction, oxidase reaction, acid / gas production from glucose and glucose oxidation / fermentation (O / F).
Table 1 shows the results of the bacteriological property test.

Figure 2011031180
Figure 2011031180

次に16S rDNA塩基配列の遺伝子解析を実施した。ゲノムDNAの抽出には、INSTAGENE MATRIX(BIO RAD, CA, USA)を使用した。抽出したゲノムDNAを鋳型として、PCRにより全塩基配列約1,500〜1,600塩基対の領域を増幅した。その後、増幅された16S rDNAをシーケンスし、塩基配列を得た。PCR産物の精製、サイクルシークエンスにはBIGDYE TERMINATOR V3.1 CYCLE SEQUENCING KIT(APPLIED BIOSYSTEMS, CA, U.S.A.)を使用した。サーマルサイクラーにはPRIMESTAR HS DNA POLYMERASE(タカラバイオ, 滋賀)、DNAシーケンサーにはABI PRISM 3100 GENETIC ANALYZER SYSTEM(APPLIED BIOSYSTEMS,
CA, U.S.A.)を使用した。なおプライマーは、文献「放線菌の同定と分類, p88-117, 日本学会事務センター, 2001.」に従った。
Next, gene analysis of 16S rDNA base sequence was performed. INSTAGENE MATRIX (BIO RAD, CA, USA) was used for extraction of genomic DNA. Using the extracted genomic DNA as a template, a region having a total base sequence of about 1,500 to 1,600 base pairs was amplified by PCR. Thereafter, the amplified 16S rDNA was sequenced to obtain a base sequence. For purification and cycle sequencing of PCR products, BIGDYE TERMINATOR V3.1 CYCLE SEQUENCING KIT (APPLIED BIOSYSTEMS, CA, USA) was used. PRIMESTAR HS DNA POLYMERASE (Takara Bio, Shiga) for thermal cyclers and ABI PRISM 3100 GENETIC ANALYZER SYSTEM (APPLIED BIOSYSTEMS, for DNA sequencers)
CA, USA). The primers were according to the document “Identification and Classification of Actinomycetes, p88-117, Japan Society for Business Administration, 2001”.

16S rDNAの塩基配列の解析結果を、バチルス属(Bacillus sp.)タテヤマ剣については配列番号1に、バチルス属(Bacillus sp.)タテヤマ薬師については配列番号2に、バチルス属(Bacillus
sp.)タテヤマ浄土については配列番号3に、アトポスティペス属(Atopostipes sp.)タテヤマ女汝については配列番号4に、クロストリディウム属(Clostridium
sp.)タテヤマ竜王については配列番号5に、それぞれ示す。
The analysis results of the base sequence of 16S rDNA are shown in SEQ ID NO: 1 for Bacillus sp. Tateyama sword, SEQ ID NO: 2 for Bacillus sp. Tateyama pharmacist, and Bacillus sp.
sp.) Tateyama Pure Land, SEQ ID NO: 3, and Atopostipes sp. Tateyama Maiden, SEQ ID NO: 4, and Clostridium.
sp.) Tateyama Ryuo is shown in SEQ ID NO: 5, respectively.

上記塩基配列をアポロンDB細菌基準株データベース(テクノスルガ, 静岡) を用いて相同性検索を行い、得られた16S rDNAの塩基配列から検体と近縁と考えられる種の相同性検索を行い、上位5株を決定した。
相同性検索結果を、バチルス属(Bacillus sp.)タテヤマ剣については表2に、バチルス属(Bacillus sp.)タテヤマ薬師については表3に、バチルス属(Bacillus
sp.)タテヤマ浄土については表4に、アトポスティペス属(Atopostipes sp.)タテヤマ女汝については表5に、クロストリディウム属(Clostridium
sp.)タテヤマ竜王については表6に、それぞれ示す。
The above base sequence is searched for homology using the Apollon DB bacterial reference strain database (Techno Suruga, Shizuoka). From the obtained 16S rDNA base sequence, a homology search for species considered to be closely related to the sample is performed. Five strains were determined.
The homology search results are shown in Table 2 for Bacillus sp. Tateyama swords, in Table 3 for Bacillus sp. Tateyama pharmacists, and Bacillus sp.
sp.) Table 4 for Tateyama Pure Land, Table 5 for Atopostipes sp. Tateyama, and Clostridium
sp.) Tateyama Ryuo is shown in Table 6, respectively.

Figure 2011031180
Figure 2011031180

Figure 2011031180
Figure 2011031180

Figure 2011031180
Figure 2011031180

Figure 2011031180
Figure 2011031180

Figure 2011031180
Figure 2011031180

これまで得られた情報をもとにCLUSTAL WとMEGA VER3.1を用いて、16S rDNA塩基配列とこれに近縁と考えられる菌群の16S rDNA塩基配列とを用いて分子系統樹を構築した。分子系統樹の推定には近隣結合法を用い、樹型の妥当性を示すブートストラップは1000回発生させた。
なお、CLUSTAL Wは文献「Nucleic Acids Research, 1994, 22:4673-4680.」、MEGAは文献「Briefings in
Bioinformatics, 2004, 5, 150-163.」に従った。
分子系統解析結果を、バチルス属(Bacillus sp.)タテヤマ剣とバチルス属(Bacillus sp.)タテヤマ薬師とについては図1に、バチルス属(Bacillus
sp.)タテヤマ浄土については図2に、アトポスティペス属(Atopostipes sp.)タテヤマ女汝については図3に、クロストリディウム属(Clostridium
sp.)については図4に、それぞれ示す。
Based on information obtained so far, CLUSTAL W and MEGA VER3.1 were used to construct a molecular phylogenetic tree using the 16S rDNA base sequence and the 16S rDNA base sequence of the bacterial group considered to be closely related thereto. . The neighbor linking method was used to estimate the molecular phylogenetic tree, and a bootstrap showing the validity of the tree type was generated 1000 times.
CLUSTAL W is a document “Nucleic Acids Research, 1994, 22: 4673-4680.” MEGA is a document “Briefings in
Bioinformatics, 2004, 5, 150-163. "
The results of molecular phylogenetic analysis are shown in FIG. 1 for the Bacillus sp. Tateyama sword and the Bacillus sp. Tateyama pharmacist.
sp.) The Tateyama Pure Land is shown in Figure 2, and the Atopostipes sp. Tateyama Lady is shown in Figure 3, Clostridium.
sp.) is shown in FIG.

好アルカリ性のバチルス属(Bacillus sp.)タテヤマ剣FERM BP-10691と、好アルカリ性のバチルス属(Bacillus sp.)タテヤマ薬師FERM BP−10692と、好塩性のバチルス属(Bacillus
sp.)タテヤマ浄土FERM BP-10693と、嫌気性菌のアトポスティペス属(Atopostipes sp.)タテヤマ女汝FERM BP-10690と、嫌気性かつ好塩性のクロストリディウム属(Clostridium sp.)タテヤマ竜王FERM BP-10694とよりなる有効微生物群2重量部をオカラ35重量部に混入し、70〜80℃の温度にて24時間一次発酵させて床材を形成した。カドミウムに汚染された土壌58重量部を床材37重量部と混合した。該土壌58重量部と該床材37重量部との混合物95重量部に、好アルカリ性のバチルス属(Bacillus sp.)タテヤマ剣FERM BP-10691と、好アルカリ性のバチルス属(Bacillus sp.)タテヤマ薬師FERM BP−10692と、好塩性のバチルス属(Bacillus
sp.)タテヤマ浄土FERM BP-10693と、嫌気性菌のアトポスティペス属(Atopostipes sp.)タテヤマ女汝FERM BP-10690と、嫌気性かつ好塩性のクロストリディウム属(Clostridium sp.)タテヤマ竜王FERM BP-10694とよりなる有効微生物群5重量部を混入し、これを60〜80℃の温度にて60時間二次発酵させた。
The alkalophilic Bacillus sp. Tateyama sword FERM BP-10691, the alkalophilic Bacillus sp. Tateyama pharmacist FERM BP-10682, and the halophilic Bacillus genus (Bacillus sp.)
sp.) Tateyama Pure Land FERM BP-10893, anaerobic bacteria Atopostipes sp. Tateyama Lady FERM BP-10690, anaerobic and halophilic Clostridium sp. 2 parts by weight of an effective microorganism group consisting of Tateyama Ryuo FERM BP-10694 was mixed in 35 parts by weight of Okara and subjected to primary fermentation at a temperature of 70 to 80 ° C. for 24 hours to form a flooring material. 58 parts by weight of soil contaminated with cadmium was mixed with 37 parts by weight of flooring. To 95 parts by weight of a mixture of 58 parts by weight of the soil and 37 parts by weight of the flooring material, an alkalophilic Bacillus sp. Tateyama sword FERM BP-10691 and an alkalophilic Bacillus sp. Tateyama pharmacist FERM BP-10692 and halophilic Bacillus
sp.) Tateyama Pure Land FERM BP-10893, anaerobic bacteria Atopostipes sp. Tateyama Lady FERM BP-10690, anaerobic and halophilic Clostridium sp. 5 parts by weight of an effective microorganism group consisting of Tateyama Ryuo FERM BP-10694 was mixed, and this was subjected to secondary fermentation at a temperature of 60 to 80 ° C. for 60 hours.

その結果、カドミウムに汚染されていた土壌は、無害化され、農作物用の安全な土壌となった。   As a result, the soil contaminated with cadmium was detoxified and became safe soil for agricultural products.

カドミウムに汚染された土壌58重量部を上記実施例1の床材37重量部と混合し、該混合物95重量部に前記有効微生物群5重量部を混入し、これをポリプロピレン製のフレコンバッグ(フレキシブルコンテナバッグ)に入れ、加温することなく1ヶ月間自然発酵させた。   58 parts by weight of soil contaminated with cadmium was mixed with 37 parts by weight of the flooring material of Example 1, and 95 parts by weight of the mixture was mixed with 5 parts by weight of the effective microorganism group. Container bag) and naturally fermented for 1 month without heating.

その結果、カドミウムに汚染されていた土壌は、無害化され、農作物用の安全な土壌となった。   As a result, the soil contaminated with cadmium was detoxified and became safe soil for agricultural products.

ダイオキシンに汚染された土壌について、上記実施例1と同じ方法を行った。その結果、ダイオキシンに汚染されていた土壌は、無害化され、農作物用の安全な土壌となった。   The same method as in Example 1 was performed on the soil contaminated with dioxin. As a result, the soil contaminated with dioxin was detoxified and became safe soil for crops.

ダイオキシンに汚染された土壌について、上記実施例2と同じ方法を行った。その結果、ダイオキシンに汚染されていた土壌は、無害化され、農作物用の安全な土壌となった。   The same method as in Example 2 was performed on the soil contaminated with dioxin. As a result, the soil contaminated with dioxin was detoxified and became safe soil for crops.

農薬と硝酸塩とに汚染された土壌について、上記実施例1と同じ方法を行った。その結果、農薬と硝酸塩とに汚染されていた土壌は、無害化され、農作物用の安全な土壌となった。   The same method as in Example 1 was performed on soil contaminated with agricultural chemicals and nitrates. As a result, soil contaminated with pesticides and nitrates was rendered harmless and became safe soil for agricultural crops.

農薬と硝酸塩とに汚染された土壌について、上記実施例2と同じ方法を行った。その結果、農薬と硝酸塩とに汚染されていた土壌は、無害化され、農作物用の安全な土壌となった。   The same method as in Example 2 was performed on soil contaminated with agricultural chemicals and nitrates. As a result, soil contaminated with pesticides and nitrates was rendered harmless and became safe soil for agricultural crops.

Claims (2)

好アルカリ性のバチルス属タテヤマ剣FERM BP-10691と、好アルカリ性のバチルス属タテヤマ薬師FERM BP−10692と、好塩性のバチルス属タテヤマ浄土FERM BP-10693と、嫌気性菌のアトポスティペス属タテヤマ女汝FERM BP-10690と、嫌気性かつ好塩性のクロストリディウム属タテヤマ竜王FERM BP-10694とよりなる有効微生物群をオカラ又は米ぬかに混入し、50〜100℃の温度にて24時間一次発酵させて床材を形成し、
被処理物を該床材と混合し、
該被処理物と該床材との混合物に、好アルカリ性のバチルス属タテヤマ剣FERM BP-10691と、好アルカリ性のバチルス属タテヤマ薬師FERM BP−10692と、好塩性のバチルス属タテヤマ浄土FERM BP-10693と、嫌気性菌のアトポスティペス属タテヤマ女汝FERM BP-10690と、嫌気性かつ好塩性のクロストリディウム属タテヤマ竜王FERM BP-10694とよりなる有効微生物群を混入し、これを60〜80℃の温度にて48〜72時間二次発酵させることを特徴とする重金属、ダイオキシン、硝酸塩及び農薬を無害化する方法。
Alkalophilic Bacillus genus sword FERM BP-10691, alkalophilic Bacillus genus Tateyama pharmacist FERM BP-10692, halophilic bacillus genus Tateyama pure soil FERM BP-10893, anaerobic bacteria Apostostis genus Tateyama有効 FERM BP-10690 and anaerobic and halophilic Clostridium genus Tateyama Ryuo FERM BP-10694 are mixed with okara or rice bran and primary at a temperature of 50-100 ° C. for 24 hours. Fermented to form flooring,
Mixing the object to be treated with the flooring;
To the mixture of the object to be treated and the flooring, an alkalophilic Bacillus genus sword FERM BP-10691, an alkalophilic Bacillus genus Tateyama pharmacist FERM BP-10692, and a halophilic Bacillus genus Tateyama pure soil FERM BP- An effective microorganism group consisting of 10893, an anaerobic bacterium, Atostipes genus TATEYAMA FERM BP-10690, and anaerobic and halophilic Clostridial genus TATEYAMA Ryuo FERM BP-10694 are mixed. A method for detoxifying heavy metals, dioxins, nitrates, and agricultural chemicals, wherein secondary fermentation is performed at a temperature of 60 to 80 ° C. for 48 to 72 hours.
好アルカリ性のバチルス属タテヤマ剣FERM BP-10691と、好アルカリ性のバチルス属タテヤマ薬師FERM BP−10692と、好塩性のバチルス属タテヤマ浄土FERM BP-10693と、嫌気性菌のアトポスティペス属タテヤマ女汝FERM BP-10690と、嫌気性かつ好塩性のクロストリディウム属タテヤマ竜王FERM BP-10694とよりなる有効微生物群をオカラ又は米ぬかに混入し、50〜100℃の温度にて24時間一次発酵させて床材を形成し、
被処理物を該床材と混合し、
該被処理物と該床材との混合物に、好アルカリ性のバチルス属タテヤマ剣FERM BP-10691と、好アルカリ性のバチルス属タテヤマ薬師FERM BP−10692と、好塩性のバチルス属タテヤマ浄土FERM BP-10693と、嫌気性菌のアトポスティペス属タテヤマ女汝FERM BP-10690と、嫌気性かつ好塩性のクロストリディウム属タテヤマ竜王FERM BP-10694とよりなる有効微生物群を混入し、これを加温することなく1〜2ヶ月間自然発酵させることを特徴とする重金属、ダイオキシン、硝酸塩及び農薬を無害化する方法。
Alkalophilic Bacillus genus sword FERM BP-10691, alkalophilic Bacillus genus Tateyama pharmacist FERM BP-10692, halophilic bacillus genus Tateyama pure soil FERM BP-10893, anaerobic bacteria Apostostis genus Tateyama有効 FERM BP-10690 and anaerobic and halophilic Clostridium genus Tateyama Ryuo FERM BP-10694 are mixed with okara or rice bran and primary at a temperature of 50-100 ° C. for 24 hours. Fermented to form flooring,
Mixing the object to be treated with the flooring;
To the mixture of the object to be treated and the flooring, an alkalophilic Bacillus genus sword FERM BP-10691, an alkalophilic Bacillus genus Tateyama pharmacist FERM BP-10692, and a halophilic Bacillus genus Tateyama pure soil FERM BP- An effective microorganism group consisting of 10893, an anaerobic bacterium, Atostipes genus TATEYAMA FERM BP-10690, and anaerobic and halophilic Clostridial genus TATEYAMA Ryuo FERM BP-10694 are mixed. A method of detoxifying heavy metals, dioxins, nitrates and agricultural chemicals, characterized by natural fermentation for 1 to 2 months without heating.
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2020155523A1 (en) * 2019-02-01 2020-08-06 中国矿业大学 Method for solidifying heavy metal of coal gangue by using microorganism
CN113245348A (en) * 2021-05-14 2021-08-13 浙江工业大学 Method for solidifying heavy metal in tailings by using halophilic bacillus
CN117862195A (en) * 2024-03-12 2024-04-12 山西青联农业科技有限公司 Method for carrying out iron tailing soil formation by utilizing ectopic ore-decomposing biological fermentation bed

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JP2008230919A (en) * 2007-03-22 2008-10-02 Suzuki Farm:Kk Method of manufacturing fertilizer, soil improvement agent or sewage treatment regulator

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008230919A (en) * 2007-03-22 2008-10-02 Suzuki Farm:Kk Method of manufacturing fertilizer, soil improvement agent or sewage treatment regulator

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2020155523A1 (en) * 2019-02-01 2020-08-06 中国矿业大学 Method for solidifying heavy metal of coal gangue by using microorganism
CN113245348A (en) * 2021-05-14 2021-08-13 浙江工业大学 Method for solidifying heavy metal in tailings by using halophilic bacillus
CN117862195A (en) * 2024-03-12 2024-04-12 山西青联农业科技有限公司 Method for carrying out iron tailing soil formation by utilizing ectopic ore-decomposing biological fermentation bed
CN117862195B (en) * 2024-03-12 2024-05-14 山西青联农业科技有限公司 Method for carrying out iron tailing soil formation by utilizing ectopic ore-decomposing biological fermentation bed

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