JPS6170987A - Method of inclusive immobilization for aerobic bacterium - Google Patents

Method of inclusive immobilization for aerobic bacterium

Info

Publication number
JPS6170987A
JPS6170987A JP59190573A JP19057384A JPS6170987A JP S6170987 A JPS6170987 A JP S6170987A JP 59190573 A JP59190573 A JP 59190573A JP 19057384 A JP19057384 A JP 19057384A JP S6170987 A JPS6170987 A JP S6170987A
Authority
JP
Japan
Prior art keywords
aerobic microorganisms
high polymer
substance
aerobic bacterium
polymer substance
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP59190573A
Other languages
Japanese (ja)
Inventor
Kaneaki Endo
銀朗 遠藤
Akira Watanabe
昭 渡辺
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Ebara Corp
Original Assignee
Ebara Infilco Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Ebara Infilco Co Ltd filed Critical Ebara Infilco Co Ltd
Priority to JP59190573A priority Critical patent/JPS6170987A/en
Publication of JPS6170987A publication Critical patent/JPS6170987A/en
Pending legal-status Critical Current

Links

Classifications

    • 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

Landscapes

  • Immobilizing And Processing Of Enzymes And Microorganisms (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

PURPOSE:To enable an aerobic bacterium to inclusive immobilization with a high polymer substance, by including the bacterium together with a specific catalytic substance capable of reducing and dissolving oxygen in air or in water in the high polymer substance. CONSTITUTION:A sulfonated metal phthalocyanine containing Fe, Cu, Ni, etc. as a metallic component, capable of reducing and dissolving oxygen in air or in water in a high polymer substance, is adsorbed on adsorbing inorganic powder (preferably carbon, apatite powder, etc.), and calcined in an inert atmo sphere at 300-800 deg.C. The prepared catalytic substance, for example, is added to suspension containing an aerobic bacterium (e.g., nitrifying bacteria, etc.) and a high polymer substance, and molded into a film, bead, etc., so that inclu sive immobization of aerobic bacterium is carried out.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、各種の産業で利用されている好気性微生換金
包括固定化する方法に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method for entrapping and immobilizing aerobic microorganisms, which is used in various industries.

〔発明の技術的背景〕[Technical background of the invention]

今日、医薬品業界及びその他の多くの業界において、 (1)菌体端度七著るしく高めることが出来ること、 (2) 有価物1Xt−短時間に生産できること、(3
)  外界の壌゛境条件の変動に対して強いこと、(4
)  取り扱いが容易であり制御もしやすぐ、さらに連
続運転が苛能でめること     −などの理由により
固定化微生物を利用した有価物質の生産に関する研究開
発が鋭意性なわれており、部分的にはすでに実用化の段
階にある。′しかしなから、これらの殆んどは酸素を全
く必要どしないか、或いは微好気的条件下でも生育し□
うる微生物を利用し友ものであり、例えば、現在各研究
機関で盛んに研究が行なわれているメタン発酵への適用
も嫌気条件下での反応である。  ゛ 一方、好気性微生物への適用上意図した幾つかの研究事
例もあるが、そのいずれもが酸素のゲル内への拡散が強
い律速となるためにその有効性が疑問視されている。
Today, in the pharmaceutical industry and many other industries, (1) it is possible to significantly increase the bacterial cell density, (2) it is possible to produce 1Xt of valuable materials in a short time, and (3)
) Must be resistant to fluctuations in the environmental conditions of the outside world, (4
) Research and development into the production of valuable substances using immobilized microorganisms is being carried out intensively for the following reasons: they are easy to handle, can be easily controlled, and can be operated continuously with extreme stress. It is already at the stage of practical application. 'However, most of these do not require any oxygen or can grow under microaerobic conditions.'
For example, methane fermentation, which is currently being actively researched at various research institutions, is a reaction under anaerobic conditions. On the other hand, there have been some research studies intended to apply it to aerobic microorganisms, but their effectiveness has been questioned because the diffusion of oxygen into the gel is a strong rate-limiting factor.

また、過酸化水素或いは過フッ化物(例えば過シッ化へ
キザンン全培地中に共存させ、グル内の酸JA濃度を高
めるなどの方法も報告されているが、長期間にわ几る微
生物活性の、維持及び培地調整の複雑さなど問題点が多
い。
In addition, methods have been reported in which hydrogen peroxide or perfluoride (for example, persulfated hexane) is coexisting in the entire medium to increase the concentration of acid JA in the gel. However, there are many problems such as the complexity of maintenance and culture medium adjustment.

〔発明の目的〕[Purpose of the invention]

本発明は、好気性微生物を包括固定化するに当り、ゲル
内へ酸素を還元溶解する触媒物質全同時に包括固定する
ことにより微生物活性を高いレベルに維持しうる包括固
定化ゲルを提供することを目的とする。
The present invention aims to provide an entrapping immobilization gel that can maintain microbial activity at a high level by simultaneously entrapping all catalyst substances that reduce and dissolve oxygen into the gel when entrapping aerobic microorganisms. purpose.

〔発明の構成〕[Structure of the invention]

本発明は、好気性微生物を高分子物質で包括固定化する
に当り、空気中又は水中の酸素を水中に還元溶解する能
力を有するスルフォン化し穴金属7タロシアニンの溶液
を吸着性無機質粉末に含浸させ、不活性ガス雰囲気中に
おいて300℃〜aOO℃の温度範囲で焼成し几後好気
性微生物と共に包括固定することを特徴とする好気性微
生物の包括固定化方法である。
In entrapping and immobilizing aerobic microorganisms with a polymeric substance, the present invention involves impregnating an adsorbent inorganic powder with a solution of sulfonated hole metal 7 talocyanine, which has the ability to reduce and dissolve oxygen in the air or water. , is a method for comprehensive immobilization of aerobic microorganisms, which is characterized in that it is calcined at a temperature range of 300° C. to aOO° C. in an inert gas atmosphere, and is then immobilized together with aerobic microorganisms.

本発明は、前記の従来の包括固定化法の有するR素の拡
散阻害という致命的欠点tスルフォン化した金属フタロ
シアニンの浴液を無機性粉末に吸着させた触媒物質會好
気注微生物と共に包括固定化することにより解決したも
ので、好気性微生物の使用を着るしく改善し効率化する
ものである。
The present invention has the fatal disadvantage of inhibiting the diffusion of R element in the conventional entrapment immobilization method.The present invention is capable of entrapping a bath solution of sulfonated metal phthalocyanine together with a catalytic substance adsorbed to an inorganic powder and an aerobic microorganism. The solution was to improve the efficiency of the use of aerobic microorganisms.

以下、本発明の詳細な説明する。The present invention will be explained in detail below.

本発明で使用するスルフォン1ヒ金属フタロシアニンの
金属成分としては、Pe、Ou、Ni  などが用いら
れ、ま几該スルフォン化金属フタロシアニン會吸着させ
る吸着性無機質担体(粉末)としては、アルミナ、シリ
カゲル、炭素或いはアパタイト粉末等が用いられるが、
炭素あるいはアパタイト粉末が好ましい。
The metal components of the sulfonated metal phthalocyanine used in the present invention include Pe, Ou, Ni, etc., and the adsorbent inorganic carrier (powder) for adsorbing the sulfonated metal phthalocyanine includes alumina, silica gel, Carbon or apatite powder is used, but
Carbon or apatite powder is preferred.

無機質担体に吸*−gせるスルフォン化金属フタロシア
ニンの量は5重量−〜50重量−位の範囲でよく、その
水浴液を無機質担体に含浸させt後乾燥しN累算囲気中
で300℃〜800℃に加熱することにより無機質担体
上にスルフォン化金属フタロシアニンを固定させる。こ
のように無機質担体上に固定することなく、あるいはス
ルフォン化金属ツタロシアエンをそのま\用いる場合、
スルフォン化金属フタロシアニンはゲル外に浴出して行
くため、所期の効果が得られない。
The amount of sulfonated metal phthalocyanine that can be absorbed into the inorganic carrier may range from 5 to 50% by weight, and the inorganic carrier is impregnated with the water bath solution, then dried at 300° C. The sulfonated metal phthalocyanine is fixed on the inorganic carrier by heating to 800°C. In this way, when using sulfonated metal tutalocyanene without fixing it on an inorganic carrier or as it is,
Since the sulfonated metal phthalocyanine leaks out of the gel, the desired effect cannot be obtained.

つぎに、本発明の好気性微生物の包括固定化方法につい
て詳しく説明する。
Next, the method for comprehensive immobilization of aerobic microorganisms of the present invention will be explained in detail.

合成、又は天然の高分子物質或いは各種のプレポリマー
浴液に細菌のけん濁液を混合して包括固定ILするに当
り、前記のようにして製造しt無機質担体上に担持され
たスルフォン化金属ツタロシアエン(以下触媒物質と略
記する)t−IS20v/v1%加え、膜状、ビーズ状
或いはキューブ状等任意の形に成形する。薄膜状に成形
し、ゲル内の触媒物質が有効にゲル外の酸素で運搬でき
るようにするのが好ましい。しかしながら、ビーズ状或
いはキューブ状に成形しても、触媒物質の濃度を高める
ことにエフ酸素の運搬は円滑に行なわれる。
When a suspension of bacteria is mixed with a synthetic or natural polymeric substance or various prepolymer bath liquids for entrapping immobilization IL, the sulfonated metal produced as described above and supported on an inorganic carrier is used. Tutalocyanene (hereinafter abbreviated as catalyst substance) t-IS 20v/v1% is added and formed into any desired shape such as a film, bead, or cube. It is preferable to form the gel into a thin film so that the catalyst substance inside the gel can be effectively transported by oxygen outside the gel. However, even when formed into beads or cubes, transport of F-oxygen is carried out smoothly by increasing the concentration of the catalyst substance.

包括固定する際に用いる細菌の濃度に、遠心等で濃縮し
次もの、あるいは培養液そのもののいずれでもよいが、
濃縮した菌体を固定する方が、短期間に高い活性が得ら
れる。
The concentration of bacteria used for comprehensive fixation can be either concentrated by centrifugation or the like, or the culture solution itself.
High activity can be obtained in a short period of time by fixing concentrated bacterial cells.

冥施例 ポリビニルアルコールを主鎖とする光硬、化性樹脂會用
い、偏性好気性菌である硝化細菌(菌体数107個/1
CC)t−包括固定化した固定化物t−1m X 5 
+o+φの円板状に成形し几ゲル状物をみかけ充填率4
0%の割合で遮2図に示す流動床タイプの反応槽に充填
、し、20℃でアンモニア合成磨水で通水しt場合の脱
アンモニアの連続実験結果を第1図に示す。
Using a light hardening resin with polyvinyl alcohol as the main chain, nitrifying bacteria that are obligate aerobic bacteria (107 bacterial cells/1
CC) t-entrapping immobilized immobilized material t-1m x 5
Formed into a disk shape of +o+φ, a gel-like substance appears and the filling rate is 4.
Figure 1 shows the results of a continuous deammonification experiment in which the fluidized bed type reaction tank shown in Figure 2 was filled with a 0% blockage ratio and water was passed through with ammonia synthetic polishing water at 20°C.

なお、触媒物質としては、鉄フタロシアニン金25重量
−の割合で骨炭粉末に吸着させ、!累算囲気中で700
℃で焼成し友もの’(1″5%(”//V)の割合で同
時に包括固定した。
In addition, as a catalyst substance, iron phthalocyanine gold is adsorbed on bone char powder at a ratio of 25 parts by weight. 700 in total
It was fired at ℃ and simultaneously fixed at a rate of 1''5% (''//V).

また、比較の几めに硝フし細菌のみt包括固定化し几ゲ
ルについても同様に試験し几。
For comparison, we also conducted the same test on a gel in which only the bacteria were immobilized using a nitrogen sieve.

第2図において、1は反応槽、2は原水導入管、5はブ
ロワ−14に包括固定化物、5.6は隔壁を示す。
In FIG. 2, 1 is a reaction tank, 2 is a raw water introduction pipe, 5 is a blower 14 containing the immobilized material, and 5.6 is a partition wall.

なお、この実施例において用い友アンモニア合成廃水の
組成は次のとおりであった−0(NH4)!804  
      15mt/l (Nとして)NaHOOs
       500 mf/1KH1P04    
   50 mW /LC&01B ” 2H1040
WLt /LNaO2180mW /L Mn804 ・7 HsO−500mW/L第1図から
明らかなように、硝化細菌と触媒物質と共に包括固定化
させた本発明の包括固定化微生物を用いた場合、硝化a
菌のみを包括固定化したものに比し格段に優れている。
The composition of the ammonia synthesis wastewater used in this example was as follows -0(NH4)! 804
15mt/l (as N) NaHOOs
500 mf/1KH1P04
50 mW /LC&01B” 2H1040
WLt /LNaO2 180mW /L Mn804 ・7 HsO-500mW/L As is clear from FIG.
It is much superior to those in which only bacteria are comprehensively immobilized.

以上説明しfI−工うに、本発f!Aは微生物固定化法
の宿命的欠陥を抜本的に改善したものであり、微生物の
固定化法の適用範flt−拡大しうるものである。
Having explained the above, the fI-work is now complete! A is a method that fundamentally improves the fatal flaws of the microorganism immobilization method, and can expand the scope of application of the microorganism immobilization method.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本発明による包括固定化物の効果金示す為の図
であり、g2図は実施例において用いた反応槽の概略図
である。 1・・反応槽、2・・原水導入管、3・・プロワ−14
・・包括固定化物
FIG. 1 is a diagram showing the effect of entrapping immobilization according to the present invention, and FIG. g2 is a schematic diagram of a reaction tank used in Examples. 1. Reaction tank, 2. Raw water introduction pipe, 3. Prower 14
・Comprehensive immobilized product

Claims (1)

【特許請求の範囲】 1、好気性微生物を高分子物質で包括固定化するに当り
、空気中又は水中の酸素を水中に還元溶解する能力を有
するスルフォン化した金属フタロシアニンの溶液を吸着
性無機質粉末に含浸させ、不活性ガス雰囲気中において 300℃〜800℃の温度範囲で焼成した後好気性微生
物と共に包括固定することを特徴とする好気性微生物の
包括固定方法。
[Claims] 1. In entrapping and immobilizing aerobic microorganisms with a polymeric substance, a solution of sulfonated metal phthalocyanine having the ability to reduce and dissolve oxygen in the air or water is used as an adsorbent inorganic powder. A method for comprehensive immobilization of aerobic microorganisms, which comprises impregnating the aerobic microorganisms with the aerobic microorganisms, calcining the mixture in an inert gas atmosphere at a temperature range of 300° C. to 800° C., and then entrapping the aerobic microorganisms together with the aerobic microorganisms.
JP59190573A 1984-09-13 1984-09-13 Method of inclusive immobilization for aerobic bacterium Pending JPS6170987A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59190573A JPS6170987A (en) 1984-09-13 1984-09-13 Method of inclusive immobilization for aerobic bacterium

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59190573A JPS6170987A (en) 1984-09-13 1984-09-13 Method of inclusive immobilization for aerobic bacterium

Publications (1)

Publication Number Publication Date
JPS6170987A true JPS6170987A (en) 1986-04-11

Family

ID=16260308

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59190573A Pending JPS6170987A (en) 1984-09-13 1984-09-13 Method of inclusive immobilization for aerobic bacterium

Country Status (1)

Country Link
JP (1) JPS6170987A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007268368A (en) * 2006-03-30 2007-10-18 Hitachi Plant Technologies Ltd Entrapping immobilization carrier and wastewater treatment system using it

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5914278A (en) * 1982-07-08 1984-01-25 アンプ・インコ−ポレ−テツド Method and device for centering electric connector

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5914278A (en) * 1982-07-08 1984-01-25 アンプ・インコ−ポレ−テツド Method and device for centering electric connector

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007268368A (en) * 2006-03-30 2007-10-18 Hitachi Plant Technologies Ltd Entrapping immobilization carrier and wastewater treatment system using it

Similar Documents

Publication Publication Date Title
US4153510A (en) High surface low volume biomass composite
CN108467118B (en) Method for removing nitrogen and phosphorus in aquaculture wastewater by using immobilized algae bacteria
CN110482715A (en) A method of synchronous nitration denitrification denitrogenation is realized using immobilized microorganism technique
CN109956563B (en) Preparation method and application of efficient aerobic denitrification phosphorus-accumulating bacteria immobilized pellet
KR101484608B1 (en) Core-shell composite having poly-vinylalcohol and alginate and method for fabricating the same
dos Santos et al. The magic-bead concept: an integrated approach to nitrogen removal with co-immobilized micro-organisms
JPH0363355B2 (en)
CN103351062B (en) Magnetic microbial carrier
CN110540947B (en) Combined microorganism nitrogen fixation preparation based on hydroxide bacteria and preparation method thereof
EP0073675B1 (en) Continuous fermentation apparatus and process
JPS62171686A (en) Production of biological group composite
JPH05507027A (en) How to remove nitrogen from an aqueous solution
CN111995066A (en) Method for treating petrochemical industry wastewater by adopting biological enhanced microbial inoculum adsorption-embedding mode
CN113003717A (en) Device and process for enhancing denitrification anaerobic methane oxidation denitrification based on magnetite
CN105087451B (en) A kind of preparation method of denitrification microorganism microbial inoculum
JPS6170987A (en) Method of inclusive immobilization for aerobic bacterium
Chen et al. Mass transfer efficiency inside the polyvinyl alcohol‐sodium alginate carriers: kinetic changes of immobilized anammox bacteria
CN113528369A (en) Preparation method and application of synchronous nitrification and denitrification bacterial agent
Wingard Jr et al. Epoxidation of propylene utilizing Nocardia corallina immobilized by gel entrapment or adsorption
Kuyukina et al. Adsorptive immobilization of rhodococcal cells in hydrophobized derivatives of wide-pore poly (acrylamide) cryogel
Yani et al. Enhancement of ammonia removal in peat biofilter seeded with enriched nitrifying bacteria
Rodionov et al. Ammonia inhibition of nitrogenase activity in purple and green bacteria
Bryers et al. [65] Application of immobilized captured microorganisms in water purification: An overview
CN107384904B (en) Immobilized heterotrophic microorganism for removing sulfide and preparation method and application thereof
WO2024124925A1 (en) Iron-carbon composite conductive particle having core-shell structure, preparation method, and use of iron-carbon composite conductive particle in wastewater anaerobic treatment