JPH0661269B2 - Microbial flocculant production enhancement method - Google Patents
Microbial flocculant production enhancement methodInfo
- Publication number
- JPH0661269B2 JPH0661269B2 JP61036023A JP3602386A JPH0661269B2 JP H0661269 B2 JPH0661269 B2 JP H0661269B2 JP 61036023 A JP61036023 A JP 61036023A JP 3602386 A JP3602386 A JP 3602386A JP H0661269 B2 JPH0661269 B2 JP H0661269B2
- Authority
- JP
- Japan
- Prior art keywords
- aeration
- microbial flocculant
- culture
- activity
- noc
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
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- Preparation Of Compounds By Using Micro-Organisms (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Treatment Of Sludge (AREA)
Description
【発明の詳細な説明】 〔技術分野〕 本発明はノカルディア・レストリクタKR-I-3(FERM4169
号)に代表されるように凝集剤生産能力を有するノカル
ディア属微生物を培養して、微生物凝集剤を製造するに
際し、炭素源、有機体窒素源を選択し、かつ初発pHを中
性からアルカリ性領域にし、過度な通気を抑えて培養す
ることにより、微生物凝集剤の生産を増強する方法に関
するものである。TECHNICAL FIELD The present invention relates to a Nocardia restrictor KR-I-3 (FERM4169).
No.) culturing a Nocardia microorganism having a flocculant-producing ability to produce a microbial flocculant, a carbon source and an organic nitrogen source are selected, and the initial pH is neutral to alkaline. The present invention relates to a method for enhancing the production of a microbial flocculant by culturing it in a region and suppressing excessive aeration.
従来、活性汚泥処理、土木浚渫処理剤として無機系凝集
剤及び合成高分子凝集剤が使用されてきた。しかしなが
ら、合成高分子凝集剤の中には、能力、経済性の面から
優れているが、ポリアクリルアミド系統のように安全性
及び二次公害の面からみて問題点が指摘されているのも
現実である。これらの問題点を克服・解消し、環境保全
の面からも、安全性の面からも、新規な凝集剤の開発は
廃水処理分野のみならずあらゆる分野から切望されてお
り、ダウンストリームプロセッシングの面からもその重
要性が認識されてきている。Conventionally, inorganic flocculants and synthetic polymer flocculants have been used as agents for treating activated sludge and civil engineering dredging. However, among the synthetic polymer flocculants, although they are superior in terms of capacity and economical efficiency, it is a reality that problems have been pointed out in terms of safety and secondary pollution as in the case of polyacrylamide type. Is. Overcoming and eliminating these problems, the development of new coagulants from the perspective of environmental protection and safety has been earnestly desired not only in the wastewater treatment field but also in all fields. The importance of this has been recognized.
そこで、本発明者らは、すでに凝集効果が大きくかつ毒
性のない微生物凝集剤NOC-1〔特許番号1096062(特公昭
56-39633号公報)〕の開発を行っており、今回、本凝集
剤のより効率的な生産増強方法について検討を進めたと
ころ、培地の栄養源を選択することにより、また培養p
H、通気量を選定することにより、極めて効果的に本凝
集剤を生産増強することを認め、本発明を完成するに至
ったものである。Therefore, the present inventors have already developed a microbial flocculant NOC-1 (Patent No. 1096062 (Japanese Patent Publication No.
56-39633)), and we are now studying a more efficient method to enhance the production of this aggregating agent.
It was confirmed that the production of the present flocculant can be enhanced very effectively by selecting H and the amount of aeration, and the present invention has been completed.
本発明によれば、ノカルディア属に属し、凝集能力を有
する微生物を培養して微生物凝集剤NOC-1を製造するに
際し、酵母エキス、カザミノ酸及びペプトンから選ばれ
る少なくとも1種を含む含有物を有機窒素源として添加
し、初発pHをpH7.0〜11.0にし、かつ次式で表される通
気比を1以下に制限して通気すること 〔R=通気比、V1=1分間当たりの常圧空気の通気量
()、V2=培養液の容量()〕 を特徴とする微生物凝集剤NOC-1の生産増強法が提供さ
れる。According to the present invention, when a microorganism belonging to the genus Nocardia and having an aggregating ability is cultured to produce a microbial aggregating agent NOC-1, a yeast extract, casamino acid, and a substance containing at least one selected from peptone are included. Add as an organic nitrogen source, adjust the initial pH to pH 7.0 to 11.0, and limit the ventilation ratio represented by the following formula to 1 or less. Provided is a method for enhancing production of a microbial flocculant NOC-1 characterized by [R = aeration ratio, V 1 = aeration amount of atmospheric air per minute (), V 2 = volume of culture solution ()]. .
なお、微生物凝集剤NOC-1(以下、微生物凝集剤とい
う)の物理化学的性質は、特公昭56-39633号公報(特許
番号1096062)に記載している。The physicochemical properties of the microbial flocculant NOC-1 (hereinafter referred to as microbial flocculant) are described in JP-B-56-39633 (Patent No. 1096062).
本発明に使用される菌株は、ノカルディア属に属し、汚
泥物質等に対し凝集能を有する菌株であればいずれでも
よいが、その代表例示菌株として、ノカルディア・レス
トリクタKR-i-3(FERM4169号)が寄託されている。The strain used in the present invention may be any strain as long as it belongs to the genus Nocardia and has a flocculating ability with respect to sludge substances and the like, as a representative exemplified strain thereof, Nocardia restrictor KR-i-3 (FERM4169 No.) has been deposited.
ところで、本凝集剤質を生産させる培地としては、これ
ら凝集能を有する微生物が生育できる培地であればどの
ような組成であっても使用できる。一般的な組成要素と
しては、炭素源及び硫酸アンモニウム、尿素等の無機窒
素源、その他、KH2PO4、MgSO4、CaCl2等の無機塩類等を含
む培地が使用されるが、望ましくは以下に示す培地組
成、培養条件で培養するのが好ましい。By the way, as the medium for producing the present flocculant, any composition can be used as long as it is a medium in which the microorganisms having the flocculating ability can grow. As a general composition element, a carbon source and ammonium sulfate, an inorganic nitrogen source such as urea, and the like, KH 2 PO 4 , MgSO 4 , a medium containing inorganic salts such as CaCl 2 is used, but preferably It is preferable to culture under the medium composition and culture conditions shown.
炭素源においては、水溶性炭素源を用いる場合には、高
生育量を示すグルコース、フラクトース等の基質を用い
ることにより高凝集活性が得られ、かつ菌の生育と凝集
活性との間に比例関係が認められる。一方、非水溶性で
あるオリーブオイルを基質に使用すると培体量に比して
凝集活性は高くはない。無機窒素源では硫安、尿素が凝
集活性に良い。有機窒素源においては、酵母エキス、カ
ザミノ酸、ペプトンにより顕著な添加効果が認められ
る。この他、至適培養初発pHは、7〜11の中性からアル
カリ性、好ましくは8.5〜9.5の弱アルカリ性領域が適し
ている。また、至適培養温度は30℃が好ましいが、25
℃、37℃においても微生物は充分な生育と凝集活性を示
す。また、通気量は、培養液に対する通気比で1以下、
好ましくは0〜0.8の範囲に制限した方が培地当りの凝
集活性が高いことが判明した。これらの結果を総合する
と従来法に比べて8倍の活性を培地当り増強させること
が可能になった。Regarding the carbon source, when a water-soluble carbon source is used, high aggregation activity can be obtained by using a substrate such as glucose or fructose that exhibits a high growth amount, and the proportional relationship between the growth and the aggregation activity of the bacterium. Is recognized. On the other hand, when water-insoluble olive oil is used as a substrate, the agglutination activity is not high compared to the amount of culture. Of the inorganic nitrogen sources, ammonium sulfate and urea are good for flocculation activity. In the organic nitrogen source, a remarkable addition effect is recognized by yeast extract, casamino acid, and peptone. In addition, the optimal initial pH of the culture is in the neutral to alkaline range of 7 to 11, preferably in the weakly alkaline range of 8.5 to 9.5. The optimum culture temperature is preferably 30 ° C, but 25
Microorganisms show sufficient growth and agglutinating activity even at 37 ° C. The aeration rate is 1 or less in terms of the aeration ratio to the culture solution,
It was found that the aggregation activity per medium was higher when the range was preferably limited to 0 to 0.8. Collecting these results, it became possible to enhance the activity per medium by 8 times compared with the conventional method.
なお、本明細書における培養液に対する通気比は、次の
式で表わされるものである。The aeration ratio to the culture solution in the present specification is represented by the following formula.
R=通気比 V1=1分間当りの常圧空気の通気量() V2=培養液の容量() ところで、微生物産生凝集剤の被凝集対象は、活性汚泥
等の有機性からカオリン等の無機性まで広範囲にわたる
が、凝集力価測定法においては、被凝集物質としてカオ
リンを選定して行った。活性は上澄液の透明度を1/濁度
で表示した。即ち、100mメスシリンダーに培養液
(物)を0.5m入れ、蒸留水で10mにフイールアップ
した後、5000ppmのカオリン懸濁液80mと10%塩化カル
シウム塩10mを加えて攪拌後、5分後の上澄液の吸光
度を波長550nmにおいて測定する。凝集活性は供試液を
用いた時の上澄の吸光度の逆数から、対照の吸光度の逆
数を差し引いた値として算出し力価とした。即ち、この
逆数の値が大きいほど透明度が大きいことを意味し、凝
集活性が高いことを示す。 R = aeration ratio V 1 = aeration amount of atmospheric air per minute () V 2 = volume of culture solution () By the way, the agglutination target of the microorganism-producing aggregating agent is kaolin or the like from organic matter such as activated sludge. Although it has a wide range of inorganic properties, kaolin was selected as the substance to be aggregated in the aggregation titer measurement method. For the activity, the transparency of the supernatant was expressed as 1 / turbidity. That is, 0.5m of culture solution (object) was put into a 100m graduated cylinder, and after being made up to 10m with distilled water, 80m of kaolin suspension of 5000ppm and 10m of 10% calcium chloride salt were added, and after stirring for 5 minutes. The absorbance of the supernatant is measured at a wavelength of 550 nm. The agglutination activity was calculated as the value obtained by subtracting the reciprocal of the absorbance of the control from the reciprocal of the absorbance of the supernatant when the test solution was used. That is, the greater the reciprocal value, the greater the transparency and the higher the aggregation activity.
次に、実施例によって本発明を更に詳しく説明する。 Next, the present invention will be described in more detail by way of examples.
実施例1 グルコース1%、尿素0.05%、K2HPO40.5%、KH2PO40.2
%、MgSO40.02%の培地に酵母エキス等の有機体窒素源
を0.05%添加した培地100mを500mの三角フラスコに
入れ、pH7.5に調整した後、120℃、15分間加圧減菌した
後、ノカルディア・レストリクタKR-I-3(FERM4169号)
を接種し、30℃にて培養し、各培養液の凝集活性の経時
変化を調べた。Example 1 Glucose 1%, Urea 0.05%, K 2 HPO 4 0.5%, KH 2 PO 4 0.2
%, MgSO 4 0.02% medium 0.05% organic nitrogen source such as yeast extract was added to 100m medium 500m Erlenmeyer flask, adjusted to pH 7.5, and sterilized under pressure at 120 ℃ for 15 minutes. Later, Nocardia Restrictor KR-I-3 (FERM4169)
Was inoculated and cultured at 30 ° C., and the time-dependent change in the aggregating activity of each culture solution was examined.
各種有機体窒素源添加による培養液0.5m当りの最大凝
集活性を表−1に示す。Table 1 shows the maximum agglutination activity per 0.5 m of the culture broth by adding various organic nitrogen sources.
これらの結果より、有機体窒素源として酵母エキス、カ
ザミノ酸、ペプトンを添加することにより培養液の凝集
活性は明らかに増大することが判明した。From these results, it was revealed that the flocculation activity of the culture solution was obviously increased by adding yeast extract, casamino acid, and peptone as the organic nitrogen source.
実施例2 実施例1の培地に有機体窒素源としての酵母エキスを0.
05%添加した培地100mを500mの三角フラスコに入
れ、培地の初発pHを6.0、7.5、8.5、9.5に調整した後、120
℃、15分間加圧減菌した後、ノカルディア・レストリク
タKR-I-3(FERM4169号)を接種し、30℃にて培養し、培
養液の凝集活性の経時変化を調べた。初発pHと各培養該
0.5m当りの最大凝集活性値を表−2に示す。 Example 2 The medium of Example 1 was supplemented with yeast extract as an organic nitrogen source.
Put 100m of the medium containing 05% into a 500m Erlenmeyer flask, adjust the initial pH of the medium to 6.0, 7.5, 8.5, 9.5, and
After sterilization under pressure at 15 ° C for 15 minutes, Nocardia restrictor KR-I-3 (FERM4169) was inoculated and cultured at 30 ° C, and the time-dependent change in aggregating activity of the culture solution was examined. Initial pH and each culture
The maximum aggregation activity value per 0.5 m is shown in Table-2.
さらに、培地の初発pHをpH10、11にしても本菌は生育
し、培養液は凝集活性をもつ。Furthermore, this bacterium grows even when the initial pH of the medium is pH 10 or 11, and the culture fluid has agglutinating activity.
以上の結果より、培養液の初発pHを中性からアルカリ性
領域にするのが凝集剤質生産には望ましいことが判明し
た。From the above results, it was found that the initial pH of the culture solution should be in the neutral to alkaline range for the production of the flocculant.
実施例3 実施例2に示す培地(pH8.5)2を卓上型ジャーファー
メーター(丸菱製、5容器)の培養槽に入れ、120
℃、15分間加圧減菌後、ノカルディア・レストリクタKR
-I-3(FERM4169号)を接種し、30℃にて毎秒500回転の攪
拌数にて通気攪拌培養した。空気の通気量はゼロ(通気
比:0)、2/min(通気比:1)、4/min(通気
比:2)の3段階に設定した。各通気比において得られ
た培養液0.5m当りの最大凝集力を表−3に示す。 Example 3 The medium (pH 8.5) 2 shown in Example 2 was placed in a culture tank of a tabletop jar fermeter (manufactured by Maruhishi, 5 containers), and 120
After sterilization under pressure at ℃ for 15 minutes, Nocardia Restrictor KR
-I-3 (FERM4169) was inoculated, and the cells were subjected to aeration and agitation culture at 30 ° C and agitation speed of 500 rpm. The air flow rate was set to three levels of zero (air flow ratio: 0), 2 / min (air flow ratio: 1), and 4 / min (air flow ratio: 2). Table 3 shows the maximum cohesive force per 0.5 m of the culture broth obtained at each aeration ratio.
この結果、過度の通気量は高活性凝集剤生産には好まし
くなく、通気比が1以下になるように空気の通気量を制
限して培養するのが望ましいことが判明した。As a result, it was found that an excessive aeration amount is not preferable for the production of the highly active flocculant, and it is desirable to limit the aeration amount of the air so that the aeration ratio is 1 or less and culture.
〔効果〕 以上の実験結果から、本発明によれば、微生物凝集剤を
効率よく生産することができる。 [Effect] From the above experimental results, according to the present invention, the microbial flocculant can be efficiently produced.
Claims (1)
微生物を培養して微生物凝集剤NOC-1を製造するに際
し、酵母エキス、カザミノ酸及びペプトンの中から選ば
れる少なくとも1種を含む含有物を有機窒素源として添
加し、初発pHをpH7.0〜11.0にし、かつ次式で表される
通気比を1以下に制限して通気することを特徴とする微
生物凝集剤NOC-1の生産増強法。 (R=通気比、V1=1分間当たりの常圧空気の通気量
()、V2=培養液の容量())1. A material containing at least one selected from yeast extract, casamino acid and peptone when a microorganism coagulant NOC-1 is produced by culturing a microorganism which belongs to the genus Nocardia and has an aggregating ability. Is added as an organic nitrogen source, the initial pH is adjusted to pH 7.0 to 11.0, and the aeration ratio represented by the following formula is limited to 1 or less for aeration to enhance the production of the microbial flocculant NOC-1. Law. (R = aeration ratio, V 1 = aeration amount of normal pressure air per minute (), V 2 = volume of culture solution ())
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61036023A JPH0661269B2 (en) | 1986-02-20 | 1986-02-20 | Microbial flocculant production enhancement method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61036023A JPH0661269B2 (en) | 1986-02-20 | 1986-02-20 | Microbial flocculant production enhancement method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS62195289A JPS62195289A (en) | 1987-08-28 |
| JPH0661269B2 true JPH0661269B2 (en) | 1994-08-17 |
Family
ID=12458125
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP61036023A Expired - Lifetime JPH0661269B2 (en) | 1986-02-20 | 1986-02-20 | Microbial flocculant production enhancement method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0661269B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107758869A (en) * | 2016-08-19 | 2018-03-06 | 辽宁惠源生物环保科技有限公司 | A kind of method that leather-making waste water is handled with microbial flocculant |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO1996019420A1 (en) * | 1994-12-20 | 1996-06-27 | Mitsuyo Kimura | Fermentation product and process for producing the same |
| CN104803545B (en) * | 2015-01-09 | 2016-11-23 | 河北德龙环境工程股份有限公司 | The using method of Water paint production wastewater suspended substance coagulant |
| CN111422995B (en) * | 2020-04-08 | 2021-01-26 | 南京御水科技有限公司 | Flocculant containing microcapsule and preparation method thereof |
Family Cites Families (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5186189A (en) * | 1974-12-25 | 1976-07-28 | Ajinomoto Kk | BISEIBUTSUNYORUTANPAKUGYOSHUKATSUSEIBUTSUSHITSUNO SEIZOHO |
| JPS5432686A (en) * | 1977-08-15 | 1979-03-10 | Agency Of Ind Science & Technol | Flocculation of microorganisms |
| JPS58183910A (en) * | 1982-04-22 | 1983-10-27 | Agency Of Ind Science & Technol | Flocculation of filthy substance by microorganism |
-
1986
- 1986-02-20 JP JP61036023A patent/JPH0661269B2/en not_active Expired - Lifetime
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107758869A (en) * | 2016-08-19 | 2018-03-06 | 辽宁惠源生物环保科技有限公司 | A kind of method that leather-making waste water is handled with microbial flocculant |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS62195289A (en) | 1987-08-28 |
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