JPS597518B2 - Wastewater coagulation treatment method - Google Patents

Wastewater coagulation treatment method

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Publication number
JPS597518B2
JPS597518B2 JP10015078A JP10015078A JPS597518B2 JP S597518 B2 JPS597518 B2 JP S597518B2 JP 10015078 A JP10015078 A JP 10015078A JP 10015078 A JP10015078 A JP 10015078A JP S597518 B2 JPS597518 B2 JP S597518B2
Authority
JP
Japan
Prior art keywords
flocculating
wastewater
active substance
culture
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.)
Expired
Application number
JP10015078A
Other languages
Japanese (ja)
Other versions
JPS5456241A (en
Inventor
智 篠原
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.)
DAIICHI TOGYO KK
Original Assignee
DAIICHI TOGYO KK
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 DAIICHI TOGYO KK filed Critical DAIICHI TOGYO KK
Priority to JP10015078A priority Critical patent/JPS597518B2/en
Priority to US05/948,227 priority patent/US4258132A/en
Priority to DE2844311A priority patent/DE2844311A1/en
Priority to FR7829017A priority patent/FR2424959A1/en
Publication of JPS5456241A publication Critical patent/JPS5456241A/en
Publication of JPS597518B2 publication Critical patent/JPS597518B2/en
Expired legal-status Critical Current

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  • Preparation Of Compounds By Using Micro-Organisms (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Description

【発明の詳細な説明】 本発明は微生物による凝集剤の利用、更に詳しくは黒色
菌科(Dematiaceae )のデマチューム(D
ematium)属に属する凝集活性物質産生菌を培養
して得られる凝集活性物質を利用して対蛋白質のみなら
ず、有機質、無機質、鉱物質、生物菌体等に対し凝集沈
降せしめる方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to the use of flocculants by microorganisms, more particularly to the use of flocculants by microorganisms, and more particularly to the use of flocculants by microorganisms, and more specifically, by the use of flocculants by microorganisms, and more specifically, by the use of flocculants by microorganisms, and more specifically, by the use of flocculants by microorganisms.
This invention relates to a method for coagulating and sedimenting not only proteins but also organic substances, inorganic substances, minerals, biological cells, etc., using a flocculant-active substance obtained by culturing a flocculant-active substance-producing bacterium belonging to the genus Ematium. .

従来においても微生物による蛋白質凝集活性物質の製法
については例えば特開昭51−86189号並びに特開
昭51=115993号等に提案されている八本発明は
これらに開示された微生物とは別個の微生物を用いて得
られる凝集活性物質な利用して蛋白質に対してのみなら
ず、有機質、無機質、鉱物質、生物菌体等が液体に懸濁
、分散、浮遊している広範なコロイド状物質に対し優れ
た凝集沈降作用を行わしめる方法を提供したものである
Conventionally, methods for producing protein aggregation active substances using microorganisms have been proposed, for example, in JP-A-51-86189 and JP-A-51-115993. The agglutinating active substance obtained using this method can be used not only for proteins, but also for a wide range of colloidal substances such as organic substances, inorganic substances, mineral substances, biological cells, etc. suspended, dispersed, or floating in liquids. This provides a method for achieving excellent flocculation and sedimentation.

本発明法に用いられる微生物は微工研菌寄番号A 4
2 5 7号の菌を含む黒色菌科(Dermtiace
ae )のデマチューム( Dema ti um )
属に属する凝集活性物質産生菌である。
The microorganism used in the method of the present invention has microorganism microorganism number A 4.
Dermtiaceae, which includes bacteria No. 2, 5, and 7.
Dematium of ae)
It is a flocculant-active substance producing bacterium belonging to the genus.

以下本発明を微工研菌寄番号A.4 2 5 7号の菌
(以下これを実施例菌と称する)を用いた場合について
説明する。
Hereinafter, the present invention will be described with reference number A. The case where the bacteria No. 4 2 5 7 (hereinafter referred to as Example bacteria) is used will be explained.

実施例菌を炭素源( glu coseSucrose
)に液体、固体培養すると菌体外に多量の凝集活性物質
を生産するが、本発明はこの凝集活性物質を各種産業廃
排水中の無機、有機の不溶性懸濁物質、コロイド物質、
不溶性、可溶性の蛋白質等を凝集除去する凝集剤として
利用する事な目的とした凝集方法を提供するものである
Example bacteria were used as a carbon source (glu case Sucrose).
), a large amount of flocculating active substance is produced outside the bacterial cells, but the present invention is capable of converting this flocculating active substance into inorganic and organic insoluble suspended solids, colloidal substances, and colloidal substances in various industrial wastewaters.
The present invention provides a flocculation method that can be used as a flocculant to flocculate and remove insoluble and soluble proteins.

本発明に用いられる凝集活性物質は菌体を含む培養液又
はその培養液を加熱殺菌して菌体を物理的、化学的に除
去した培養液或いはこの培養液を有機溶剤で精製して得
た固形物質等シ意味する。
The flocculating active substance used in the present invention is obtained from a culture solution containing bacterial cells, a culture solution obtained by heating and sterilizing the culture solution to physically or chemically remove the bacterial cells, or by purifying this culture solution with an organic solvent. means solid substances, etc.

又本発明の適用を受ける各種廃排水には蓄産排水、食品
工業排水、パルプ排水その他の産業廃排水をあげること
ができる。
Various types of wastewater to which the present invention is applied include accumulated wastewater, food industry wastewater, pulp wastewater, and other industrial wastewater.

各種産業廃排水への本凝集活性吻質の添加は液体又は固
体で添加し、添加量は廃排水の質によって変化するが、
数ppm〜数十p pmである。
This flocculating active rostol is added to various types of industrial wastewater in the form of liquid or solid, and the amount added varies depending on the quality of the wastewater.
The amount ranges from several ppm to several tens of ppm.

添加方法は廃排水k 6 0 rpm/minで攪拌し
その液に本凝集活性物質な加え、数分後硫酸アルミニウ
ムを添加し攪拌すると数分(1〜2分)で凝集が起り、
そのフロックの形成は早く、沈降性は著しく良い。
The method of addition is to stir the wastewater at 60 rpm/min, add this flocculating active substance to the liquid, add aluminum sulfate after a few minutes, and stir, and flocculation will occur in a few minutes (1 to 2 minutes).
Its floc formation is fast and its settling properties are very good.

上澄液の濁度は720nμでT%な測定し、蒸留水を対
照にして比較した。
The turbidity of the supernatant liquid was measured as T% at 720 nμ and compared with distilled water as a control.

CODはJIS方で分析し、色価は420nμで測定、
処理液のpHは処理水の質によって変動させ、又硫酸ア
ルミニウム添加量もその質によって変動させた。
COD is analyzed by JIS method, color value is measured at 420nμ,
The pH of the treatment solution was varied depending on the quality of the treated water, and the amount of aluminum sulfate added was also varied depending on the quality.

供試した産業廃排水については特長の著しい廃排水につ
いて試験した。
Among the industrial wastewater samples tested, wastewater with remarkable characteristics was tested.

以下具体的な実施例を述べるが、以下参考までに前記の
実施例菌の菌学的特徴について説明すると次qクである
Specific Examples will be described below, but for reference, the mycological characteristics of the bacteria of the Examples are explained below.

A 分離菌の菌学的特徴 コロニーは初め表面乎渭で灰白色、粘液性、光沢ある油
滴状(脂肪様)の酵母様に発育し、その周縁から糸状の
菌体が放射状に成長し、ちぢれた様な糸状で丁度樹枝状
発育をする。
A. Mycological characteristics of the isolated bacteria Colonies initially grow on the surface as grayish-white, slimy, glossy, oil drop-shaped (fat-like) yeast-like cells, and filamentous bacterial bodies grow radially from the periphery and become curly. It is filamentous and develops like a tree.

この糸状菌体は培地表面のみならず培地中にもよく発育
する。
These filamentous fungi grow well not only on the surface of the medium but also inside the medium.

しばらくすると、コロニー表面に淡暗褐色の斑点が点々
と現われ次第に黒色の斑点になシ遂に全面が暗黒色とな
る。
After a while, light brown spots appear on the surface of the colony, which gradually turn into black spots, and finally the entire surface becomes dark black.

この糸状菌体に淡褐色の楕円又は卵形の多数の分生子を
側生ずる。
This filamentous fungus produces many pale brown oval or oval conidia.

この分生子は容易にばらばらになる。These conidia easily break apart.

一方油滴状のコロニーの表面にも点々と分生子をつける
On the other hand, conidia are also attached to the surface of the oil droplet-shaped colony.

糖類を含んだ培養液は非常に粘稠性とな択液面に厚いコ
ロニーで皮革の黒色培苔を生ずる。
The culture solution containing sugars becomes very viscous and produces thick colonies of leathery black moss on the surface of the solution.

最適発育温度は20〜25℃でブドウ糖、シヨ糖などの
糖類からアルコール類、有機酸類を生成し、又特有の芳
香を有する。
The optimum growth temperature is 20 to 25°C, at which alcohols and organic acids are produced from sugars such as glucose and sucrose, and it also has a unique aroma.

1 培養的特徴黄.(注) ■ 固体培地:バレイショ、グルコース寒天培地上、最
初コロニーは表面平渭、透明、光沢ある油滴状、粘稠性
の灰白色の酵母様で、コロニーの周縁から放射状にちぢ
れた糸状様の丁度樹枝状の菌体が発育し、この糸状様菌
体は培地表面のみならず、培地中にもよく発育する。
1 Cultural characteristics: yellow. (Note) ■ Solid medium: Potato, on glucose agar medium. At first, the colony has a flat surface, is transparent, has a glossy oil drop shape, and is viscous, grayish-white, yeast-like, and has a filament-like shape that curls radially from the periphery of the colony. Just dendritic fungal cells grow, and these filamentous fungal cells grow well not only on the surface of the medium but also inside the medium.

やがてその樹枝様のところどころの部分が黒褐色になる
Eventually, some parts of the tree-like branches turn blackish brown.

培養して3〜4日たつとコロニー表面に淡暗褐色の斑点
が点々と現われるが、以後次第に淡暗黒色になり全面に
広がり、遂に全体が黒色になる(培養7日)。
After 3 to 4 days of culturing, light brown spots appear on the surface of the colony, which gradually becomes dark black and spreads over the entire surface, and finally becomes black as a whole (after 7 days of culture).

尚ツアベック寒天培地上では発育がおそいが、培養的特
徴は前記の様であるコロニー表面が全面黒色になるのに
3週間くらいかかる。
Although growth is slow on Zuavec agar medium, the culture characteristics are as described above. It takes about 3 weeks for the colony surface to become completely black.

@ 液体培養:バレイショ、グルコース培地中点点浮遊
状態に菌体が発育し(培養3日)、次第にコロニーが増
え、やがて(培養7日)液中に粘性の7ロニーが充満す
る。
@Liquid culture: Potato and glucose medium Midpoint Bacterial cells grow in a floating state (3 days of culture), colonies gradually increase, and eventually (7 days of culture) the liquid is filled with viscous 7 Rony.

そして管壁に暗黒色の菌苔が現われ、次第に液面にも出
来る(培養15日)。
Then, dark black fungal moss appeared on the tube wall and gradually formed on the liquid surface (15 days of culture).

この菌蓋はゼラチナスな粘性のある厚いものである。This fungal lid is thick and gelatinous.

尚ツアベック培地中にも同様に発育するが、非常におそ
く菌体も少く、約3週間培養で液面にかなりの黒色菌苔
なつくる。
Although it grows in the same way in Zuavec medium, it is very slow and the number of bacterial cells is small, and after about 3 weeks of culturing, a considerable black fungus moss is formed on the liquid surface.

2 形態的特徴 若い細胞は透明な糸状のちぢれた樹枝状で、菌体(糸状
様)はところどころから黒く卵形の胞子様のものが側生
ずる。
2. Morphological characteristics The young cells are transparent, filamentous, curly, and arborescent, and the fungal cells (filamentous) have black, oval, spore-like bodies growing laterally here and there.

又油滴状のコロニーはその中に点々と黒色の胞子様のも
のが着生する。
In addition, the oil drop-shaped colonies have black spore-like substances attached to them.

これは衝撃なあたえるとばらばらになる。This will fall apart if you give it a shock.

3 生理的特徴 最適発育温度は20〜25℃、グルコース、シュークロ
ーズなどから粘性物を生成文グルコースなどの糖類から
アルコール類、有機酸類を生ずる特有の芳香を有する。
3 Physiological Characteristics Optimal growth temperature is 20-25°C. Viscous substances are produced from glucose, sucrose, etc. Alcohols and organic acids are produced from sugars such as glucose. It has a unique aroma.

黄■文献として G e o rg e SMITH著 応用菌学指針
(An introduction to ind
ustrialmycology)( p6 8 〜9
7)応用微生物学各論(p83〜87) に準拠。
Yellow ■References include An introduction to ind. by George Smith.
(ustrialmycology) (p6 8-9
7) Based on Applied Microbiology (pages 83-87).

B 菌の分離と凝集性の検出 菌の分離培地として原糖の5係の溶液を作り、常法で殺
菌し、1 0 0fnlの三角フラスコに20一分注し
pHを微酸性に調整後再度殺菌し、この液体培地に下記
に記述した原液を1rrIlずつ添加し、静置法で(室
淵25〜30℃)培養し、一日毎にサンプリングして凝
集性を調べた。
B Isolation of bacteria and detection of flocculation Make a 5-part solution of raw sugar as a bacterial isolation medium, sterilize it in the usual way, pour it into a 100 fnl Erlenmeyer flask, adjust the pH to slightly acidic, and then pour it again. After sterilization, 1 rrl of the stock solution described below was added to this liquid medium, cultured by a static method (Murobuchi 25-30°C), and samples were taken every day to examine aggregation.

即ち通常凝集試験に使用するカオリン(武田薬品製の試
薬特級)の1%溶液を作り、pHを微酸はとして供試液
とした。
That is, a 1% solution of kaolin (special grade reagent manufactured by Takeda Pharmaceutical Co., Ltd.), which is normally used in agglutination tests, was prepared, and the pH was adjusted to slightly acidic to prepare a test solution.

上記の原液はグラニュー糖、原糖に含まれている高分子
多糖の分離、分析中ビーカーに長時間放置していた原糖
の希薄溶液(24A(径口)のセルローズ膜で透析した
液)の粘性が高くなっている事に気付き、再度透析をす
る為にE過なしたものである。
The above stock solution is a dilute solution of granulated sugar, a dilute solution of raw sugar that had been left in a beaker for a long time during analysis (a solution dialyzed with a 24A (diameter) cellulose membrane). I noticed that the viscosity had increased, so I went through E to undergo dialysis again.

その操作に於て硅藻土又は活性炭素な少量添加した時本
溶液が非常に著しい凝集性、即ち硅礫土又は活性炭素が
一瞬にしてビーカーの底部に凝固し他の市販凝集剤には
見られない凝集力がある事を発見した。
During the operation, when a small amount of diatomaceous earth or activated carbon is added, this solution exhibits a very significant flocculating property, i.e., the diatomaceous earth or activated carbon instantly solidifies at the bottom of the beaker, unlike other commercially available flocculants. I discovered that there is no cohesive force.

更に本溶液に種々の物質、カオリン、ベントナイト等の
ケイ酸アルミニウムを主成分とする物質又無機物質、即
ち炭酸カルシウム、髄酸バリウム、塩化銀等の中性塩、
有機物質を添加するといづれも著しい凝集をする事な定
性的に確認した。
Furthermore, various substances, such as kaolin, bentonite, etc., containing aluminum silicate as a main component, or inorganic substances, i.e., neutral salts such as calcium carbonate, barium myelate, silver chloride, etc., are added to this solution.
It was qualitatively confirmed that no significant aggregation occurred when organic substances were added.

この凝集試験には本供試液を50一の試験管に25rr
ll*D, これに培養液を1一添加し上下に10回
撹拌後3分間静止しその上澄液の濁度を光電比色計を使
用し#で濁 度を測定した。
For this agglutination test, add 25rr of this sample solution to 50 test tubes.
ll*D, 11 times of the culture solution was added to this, stirred up and down 10 times, and then allowed to stand still for 3 minutes.The turbidity of the supernatant was measured using a photoelectric colorimeter.

又上澄液中に残留するカオリン量な重量法で測定し彎集
性を調べた結果、初期検養時間の培養液からその凝集性
は著しい。
In addition, the amount of kaolin remaining in the supernatant liquid was measured by gravimetric method and the flocculation property was investigated. As a result, the flocculation property was remarkable from the culture solution at the initial testing time.

この事は培地中に代謝される本凝隼活性物質は微量、で
凝集作用がある事を示唆している。
This suggests that the flocculant active substance metabolized into the medium has an aggregating effect even in small amounts.

尚培養時間の経過と共に(96時間)アセトン、ブタノ
ール.臭腔彷くなった。
As the culture time progresses (96 hours), acetone, butanol. I started wandering around the smelly room.

そこで培養時間を72時間とし正、この培養な10回く
シ返して凝集力の強い培養液でアセトン、プタノール臭
がなく、本培養液特有の香気(バラの花の香気)を有す
る培養液な選びこの液から本菌の純粋?行った。
Therefore, the culture time was set to 72 hours, and the culture was repeated 10 times to produce a culture solution with strong cohesive force, no acetone or putanol odor, and a culture solution with a unique aroma (rose flower aroma). Is this fungus pure from this liquid? went.

本菌の純粋分離〜原糖又はシュークローズ(燕糖)の5
チ溶液を作りp.H5〜6に調整し更に粉末酵母エキス
(武田薬品製)を0.2%添加し、寒天( 0. 1
6%)を加え常法によシ加熱殺菌し、シャーレに分注し
て分離培地とした。
Pure isolation of this bacterium ~ raw sugar or sucrose (swallow sugar) 5
Make a p. Adjust to H5-6, add 0.2% powdered yeast extract (manufactured by Takeda Pharmaceutical), and add agar (0.1%).
6%) was added, heat sterilized by a conventional method, and dispensed into petri dishes to prepare a separation medium.

これに培養液を殺菌水で100倍、200倍、500倍
に稀釈してシャーレにlrnl分注し30℃で培養した
The culture solution was diluted 100 times, 200 times, and 500 times with sterilized water, and lrnl aliquots were poured into petri dishes and cultured at 30°C.

その結果3種類のコロニーを検出し、更にスラント培養
、液体培養をくり返して3種類の菌を純粋に分離した。
As a result, three types of colonies were detected, and slant culture and liquid culture were repeated to isolate pure three types of bacteria.

培養初期のコロニーは(培養時間48時間前後)全べて
クリーム色であるが、時間の経過とともにコロニーの表
面中央部が黒色となり更に時間が経過するとコロニーの
裏面に黒い菌糸がコロニーを中心にして培地に植根状に
延びてくる菌を分離菌■とする。
All colonies at the initial stage of culture (around 48 hours of culture) are cream-colored, but as time passes, the center of the surface of the colony becomes black, and as time passes, black hyphae appear on the back of the colony, centered around the colony. The bacteria that grows into the medium in a root-like manner are called isolated bacteria ■.

クリーム色コロニーが時間の経過で変色もせずもシあが
る菌を分離菌■、更にクリーム色が培養時間とともに褐
色になる菌を分離菌■とする。
A bacterium whose cream-colored colony fades without changing color with the passage of time is called an isolated bacterium (■), and a bacterium whose cream color turns brown with the passage of incubation time is called an isolated bacterium (■).

分離した3種類の菌を上記組成の培養液で静置培養し、
その培養液の凝集力をカオリン1係溶液を使用して調べ
た。
The three types of isolated bacteria were statically cultured in a culture solution with the above composition,
The cohesive force of the culture solution was examined using a kaolin 1 solution.

その結果は分離菌■、即ちコロニー表面が時間の経過と
ともに黒色となり、更に裏面に黒い菌糸が植根状に延び
る菌にのみ凝集性があり、本培養液の児掛上の粘註は培
養時間とともに増加し、更に本菌に特有の香気(バラの
花の香気)を検出した。
The results showed that only isolated bacteria ■, that is, bacteria whose colony surface turns black over time and black hyphae extend like roots on the back side, have flocculating properties, and the viscosity on the brood of the main culture solution changes over time. In addition, an aroma unique to this fungus (rose flower aroma) was detected.

他の分離菌■,■の培養液には凝集性を検出せず、分離
菌■ではアセトン臭を、分離菌■では酪酸臭を検出した
No aggregation was detected in the culture solutions of the other isolated bacteria ■ and ■, but an acetone odor was detected for the isolated bacteria ■, and a butyric acid odor was detected for the isolated bacteria ■.

この分離菌■が黒色菌科(Dematiaceae)の
デマチューム(Dematium)属に属する凝集活性
物質産生菌である。
This isolated bacterium (1) is a flocculating active substance-producing bacterium belonging to the genus Dematium of the family Dematiaceae.

C 分離菌■を使用しての培養と凝集物質の生産純粋に
分離した菌I ( Dem ati aceaeのDe
ma−tium属)を使用しての凝集物質の生産、培養
条件の結果は下記の通りである。
C Cultivation and production of flocculants using isolated bacteria ■ Purely isolated bacteria I (Demati aceae De
The results of the production of aggregated substances using the genus Ma-tium and the culture conditions are as follows.

炭素源としてグルコース、フラクトース、ガラクトース
等のヘキソーズ又はシュークローズ等の二糖類、澱分等
の多糖を使用しこれに酵母エキスを0.2%添力哄て静
置法で培養し1週間後に培養液の凝集性を調ラたがいず
れの場合も凝集性を有する培養液を得丸又通常使用する
合成培地例えばCZapeke(ツアペク)培地に炭素
源としてグルコース等を入れるだけで凝集物質を培養液
に生産する。
Using hexoses such as glucose, fructose, and galactose, or disaccharides such as sucrose, and polysaccharides such as lees as a carbon source, add 0.2% yeast extract to this, culture by standing method, and culture after 1 week. The flocculating properties of the liquid were adjusted, but in any case, a culture medium with flocculating properties was obtained.By simply adding glucose, etc. as a carbon source to a commonly used synthetic medium, such as CZapeke medium, flocculating substances could be added to the culture medium. Produce.

上述の如く炭水化物を主成分とする単純な培地組成で凝
集物質を培養液に産出する事がわかった。
As mentioned above, it was found that a simple medium composition containing carbohydrates as the main component produced aggregated substances in the culture solution.

例えば原糖を炭素源として使用すれば他の栄養素(N素
源無機質等)を添加する事が必要でない。
For example, if raw sugar is used as a carbon source, it is not necessary to add other nutrients (N source minerals, etc.).

炭素源の培地濃度を5〜20%にして培養した結束、濃
度が増加するにつれて基質に対する凝集物質の生産量が
低下し、5係前後が良い事が判明した。
It was found that as the concentration of the carbon source in the medium was cultured at a concentration of 5 to 20%, the production amount of flocculating substances with respect to the substrate decreased as the concentration increased, and that a ratio of around 5 was good.

即ち本凝集物質の粘性が非常に高い為、本物質が一定濃
度になると菌の成長が物理的に阻害されると判断した。
In other words, since the viscosity of this flocculating substance is extremely high, it was determined that the growth of bacteria would be physically inhibited when this substance reached a certain concentration.

pHは初期に微酸性に調整しておけば特に厳密な調整を
必要としない。
The pH does not require particularly strict adjustment if it is initially adjusted to be slightly acidic.

培養経過中に多少酸性に低下する。It becomes slightly acidic during the course of culture.

静置又は振盪培養とも凝集物質を産出するが、振盪培養
の方が凝集物質生成が早い事が判明した。
Both static and shaking culture produce aggregated substances, but it was found that shaking culture produces aggregated substances faster.

本凝集物質の基質(炭素源)に対する収量は10%以上
であり、基質濃度に逆比例する。
The yield of this flocculating substance based on the substrate (carbon source) is 10% or more and is inversely proportional to the substrate concentration.

培養条件、培地素成 炭素源 グルコース 濃度5係 フラクトース 5% グラニュー糖 5係 原 糖 5係 N源素 粉末酵母を原糖以外の培地に 0.2係添加 pH 5.0にHCtで調整 温度28〜30℃ 接種菌は本分離菌■を7日間振盪培養した培養液をlr
r1l添加した。
Culture conditions, medium, elementary carbon source, glucose, concentration 5, fructose, 5%, granulated sugar, concentration 5, raw sugar, 5% N source, powdered yeast added to the medium other than raw sugar at 0.2 volume, pH adjusted to 5.0 with HCt, temperature 28 ~30℃ The inoculum is a culture solution obtained by culturing this isolate ■ with shaking for 7 days.
r1l was added.

D 本分離菌■が産出する凝集物質の分離精製法■ 上記の培養条件の培地に分離菌■(黒色菌科のDema
tium属)な接種して培養した培養液を加熱し(10
0℃/5分)、遠沈如理3,0 0 0 rpn/mi
n(,て菌体を除去又はF過、分離して菌体を除去し分
離液にエタノールを30〜40%濃度になる様に添加す
ると(アセトン、メタノールでもよい)エタノールと培
養液の液面に薄膜力注し、攬拌すると瞬時に繊維状又は
綿状の物質が1ケ所に凝集する。
D Separation and purification method of flocculated substances produced by this isolated bacterium
tium genus) was inoculated and cultured, the culture solution was heated (10
0°C/5 minutes), centrifugation 3,000 rpn/mi
When the bacterial cells are removed by filtration or filtration, and ethanol is added to the separated solution to a concentration of 30 to 40% (acetone or methanol may be used), the liquid level of the ethanol and culture solution increases. When a thin film is poured into the liquid and stirred, the fibrous or cotton-like substance instantly aggregates in one place.

凝集した物質を一心分離又は攪拌棒に附着させて分離し
、再度水に溶解させエタノールを添加し再凝集させ、分
一減圧乾燥すると凝集物質が得られる。
The aggregated substance is separated by single-center separation or attached to a stirring rod, dissolved in water again, ethanol is added to cause re-agglomeration, and the aggregated substance is obtained by drying under reduced pressure.

分離した凝集物質は灰白色で粉末状にする事は容易であ
る。
The separated aggregated substance is grayish white and can be easily powdered.

尚本物質は低濃度のエチルアルコールで瞬時に凝集する
事から均一な高分子量物質である事が推論される。
It is inferred that this substance is a homogeneous high-molecular-weight substance because it coagulates instantaneously with low concentration of ethyl alcohol.

分離精製法■ 培養液中の凝集物質は酸性に於て、アルミニウムイオン
を添加すると著しい凝集をし、アルカリ性に於ではカル
シウムイオンにより凝集する事を見出した。
Separation and Purification Method■ It was found that the flocculating substances in the culture solution flocculate significantly when aluminum ions are added in acidic conditions, and that they flocculate due to calcium ions in alkaline conditions.

添加するアルミニウムイオンとしては備酸アルミニウム
又はその重合体で、カルシウムイオンは塩化物として、
又石灰等である。
The aluminum ion to be added is aluminum chloride or its polymer, and the calcium ion is added as a chloride.
Also, lime etc.

この性a−ら培養液中の凝集物質を分離する方法な確立
した。
A method for separating aggregated substances in a culture solution was established.

即ち培養液を加熱処理後(100℃/5分)E過又は遠
心処理で菌体を除し、菌体な除去した液に0.05〜0
.10%の無機イオン、即ち液を酸性にした時はアルミ
ニウム化合物、アルカリの時; はカルシウム化合物?
加え攪拌すると本凝集物質が完全に凝集してくる。
That is, after heat-treating the culture solution (100°C/5 minutes), bacterial cells are removed by E-filtering or centrifugation, and 0.05-0.
.. Is the 10% inorganic ion, that is, an aluminum compound when the liquid is acidic, and a calcium compound when the liquid is alkaline?
When added and stirred, the flocculated substance will be completely flocculated.

これをE過又は遠心処理して分離し乾燥して固型粉末の
凝集物質を得る事が出来る。
This can be separated by E filtration or centrifugation, and dried to obtain a solid powdery agglomerated substance.

分離精製法■ ; 培養液を加熱処理後(100℃/5分)菌体な除去
し、菌体を含有しない液を濃縮して(10%前後)凝集
剤とする。
Separation and purification method ①; After heat-treating the culture solution (100° C./5 minutes), remove the microbial cells, and concentrate the solution containing no microbial cells (approximately 10%) to use as a flocculant.

工業的に凝集剤として使用する時は本物質が非常に安定
した物質である事と、使用時に溶解の必要性がない事な
ど使用上、製造冫 上液体で増扱う事が非常に合理的で
ある。
When used industrially as a flocculant, it is very rational to use it as a liquid during production, as this substance is a very stable substance and does not require dissolution during use. be.

下表に本物質(凝集物質)の分離、精製法を一括して示
す。
The table below summarizes the separation and purification methods for this substance (agglomerated substance).

無機塩添加による本物質の分離、分離法■は本物質と無
機塩が定量的に反応する為に培養液中の本物質の濃度を
定量しておき計算量の無機頃を添加する。
Separation of this substance by addition of inorganic salt, Separation method (2) involves quantifying the concentration of this substance in the culture solution and adding the calculated amount of inorganic salt, since this substance and inorganic salt react quantitatively.

尚分離法■の残液は多少炭素源が残留している為に培養
に適したpHに調整してくり返し使用する。
Since the residual liquid from separation method (2) contains some residual carbon source, it is adjusted to a pH suitable for culture and used repeatedly.

添加したアルミニウム等の無機イオンは本菌の培養阻害
剤にはならなへ E 凝集剤としての使用又は利用 分離菌■、即ち黒色菌科のDematium属を培養し
、上記分離法で得られた。
The added inorganic ions, such as aluminum, do not act as culture inhibitors for the bacteria.Use or use as a flocculant.Isolated bacteria (1), ie, Dematium genus of the family Black Mycoceae, was cultured and obtained by the above separation method.

液体、固体又無機イオンを含む固体凝集物質は非常に微
量で、即ち液量に対して0.1ppm〜2.0ppm添
加する事により水又は水を含む液体に分散、懸濁、コロ
イド状、浮遊する有機、無機物質又は生物菌体を完全に
凝集沈澱させる性質がある事を発見した。
Liquids, solids, and solid aggregates containing inorganic ions can be dispersed, suspended, colloidal, or suspended in water or water-containing liquids by adding very small amounts of 0.1 to 2.0 ppm based on the amount of liquid. It was discovered that it has the property of completely coagulating and precipitating organic and inorganic substances and biological bacteria.

尚本物質の凝集作用は現有市販凝集剤(無機、有機)に
比較すると著しく強いといえる。
It should be noted that the flocculating effect of this substance is significantly stronger than that of existing commercially available flocculants (inorganic and organic).

又微生物の代謝物質である為に凝集剤による二次汚染の
問題もないメリットを有している。
Furthermore, since it is a metabolite of microorganisms, it has the advantage of not having the problem of secondary contamination caused by flocculants.

凝集時の条件は暉至適pHの範囲は酸性〜微酸性でアル
カリ性では十分な凝集力は示さない。
The optimum pH range for aggregation is acidic to slightly acidic; alkaline conditions do not provide sufficient cohesion.

■反応潟度は常温から高温まで凝集力に関係ない。■The reaction lagoon is unrelated to the cohesive force from room temperature to high temperature.

■本凝集物質添加後、緩やかな攪拌なするのが有利であ
る。
(2) It is advantageous to perform gentle stirring after adding the flocculating substance.

■凝集剤としての使用量は0.1p″pm〜3.Opp
m でよく、使用量は特殊物質を除いて凝集させられる
物質には関係ない。
■The amount used as a flocculant is 0.1p″pm to 3.Opp
m may be sufficient, and the amount used is not related to substances to be aggregated except for special substances.

酸性側に於て本凝集活性物質では凝集しない物質、例え
ばセルローズ粉末、澱分粒子等の水溶液では本凝集活性
物質を添加攪拌後、添加した凝集活性物質のl/30〜
l/40量のアルミニウムイオンを添加して撹拌すると
、セルローズ粉末、澱粉粒子等は一瞬にして凝集沈澱す
る事を発見した。
On the acidic side, for substances that do not agglomerate with this agglomerating active substance, such as cellulose powder, starch particles, etc., this aggregating active substance is added and stirred, and then 1/30 to 1/30 of the added aggregating active substance is added.
It was discovered that when 1/40 of aluminum ions were added and stirred, cellulose powder, starch particles, etc. coagulated and precipitated instantly.

この事はより、酸性側に於で水に懸濁、分散、浮遊、コ
ロイド状で存在する有機、有機物質は全べて凝集沈澱さ
せる事ができた。
This means that on the acidic side, all organic substances that are suspended, dispersed, floating, or colloidal in water can be coagulated and precipitated.

アルカリ側に於ける本凝集甜物質の凝集力は非常に微弱
ではあるが、カルシウムイ穿ンを添加する事によりその
凝集力はm側に於ける本物質の凝集力と同様になる事を
発見した。
Although the cohesive force of this cohesive substance on the alkaline side is very weak, it was discovered that by adding calcium ipane, the cohesive force becomes similar to the cohesive force of this substance on the m side. did.

カルシウムイオンの添加量は酸性側に於けるアルミニウ
ムイオン添加量より多く、添加した本凝集物質量の20
〜30倍量、即ち40〜80ppm を必要とする。
The amount of calcium ions added is greater than the amount of aluminum ions added on the acidic side, and is
-30 times the amount, i.e. 40-80 ppm is required.

この実験結果から全べてpH領域に於て本凝集活性物質
は微量で水に懸濁、分散、浮遊、コロイド状に存在する
有機、無機吻質な凝集沈澱させる事が出来る事を可能に
した。
The results of this experiment showed that in all pH ranges, this flocculating active substance can be suspended, dispersed, floated, and colloidally present in water in a very small amount, making it possible to flocculate and precipitate organic and inorganic substances. .

本物質の凝集作用は、本物質がきわめて均一な高分子量
で水に対する親和力が非常に高いので(この推論は低濃
度のアルコールで瞬時に凝集する事から出来る)あたか
も水の中にきめのこまかい網を均一に詰めこんだ状態で
水と水和しているが、これに荷電した微粒子又は無機物
質が入ると、その分散した網が電気的にバランスを失い
凝集する時あたかも網で魚を捕える様に物質な捕えると
推論する。
The aggregation effect of this substance is due to its extremely uniform high molecular weight and extremely high affinity for water (this inference can be made from the fact that it coagulates instantly with low concentration of alcohol), as if it were a fine-grained net in water. When charged particles or inorganic substances enter this uniformly packed state, the dispersed net loses its electrical balance and clumps together, just like catching fish with a net. Material capture and inference.

この事はアルミニウムイオンを本凝集活性物質の水溶液
に微量添加した時の凝集?観察する事により明瞭となる
Does this mean that aluminum ions are flocculated when a small amount is added to the aqueous solution of this flocculating active substance? It becomes clear through observation.

・又本凝集活性物質の溶液にエタノールな添加するとそ
の境界面に薄膜がコロヂオン膜を作る時の様に生じこの
様な膜がいくえにも重なっている事を観察出来る。
・Also, when ethanol is added to a solution of this flocculating active substance, a thin film is formed on the interface, similar to when a collodion film is formed, and it can be observed that many such films overlap.

尚本凝集物質は使用時に於て水溶液として使用する。The flocculating substance is used in the form of an aqueous solution.

又精製法■によって得られたアルミニウム含有凝集物質
、カルシウム含有凝集活性物質は使用時にアルカリ又は
酸性の水溶液として使用する。
In addition, the aluminum-containing flocculating substance and calcium-containing flocculating active substance obtained by purification method (1) are used as an alkaline or acidic aqueous solution.

F 本活性物質の物理化学的性質 エタノールで分離精製した本凝集活性物質は水に可溶で
その0.1%の水溶液の比粘度は4〜5であり砂糖の4
0係溶液の粘度に相当する。
F Physical and chemical properties of this active substance This flocculated active substance separated and purified with ethanol is soluble in water, and the specific viscosity of a 0.1% aqueous solution is 4 to 5, which is 4
Corresponds to the viscosity of a zero coefficient solution.

本凝集活性物質のアンスロン、モーリツシュ、ピューレ
ット反応はいずれも■であり、カルバゾール反応による
一COOH基の定性反応も■でその定量値をガラクチュ
ロン酸で示すと、その含有量は10〜15係である。
The Anthrone, Mauritsch, and Puret reactions of this flocculating active substance are all ■, and the qualitative reaction of one COOH group by carbazole reaction is also ■, and when the quantitative value is expressed as galacturonic acid, the content is 10 to 15. be.

又INH2SO4で24時間加水分解した際に未分解物
質が残留し加水分解液の糖組成はペーパークロマトで、
グルコース、ガラクトース、マンノース等の糖を検出し
た。
Also, when hydrolyzed with INH2SO4 for 24 hours, undecomposed substances remained, and the sugar composition of the hydrolyzed solution was determined by paper chromatography.
Sugars such as glucose, galactose, and mannose were detected.

この赤外クロマトでは一COOH の吸収が確認された
が、アミド基等についてはその吸収が明瞭でなかった。
In this infrared chromatography, absorption of 1-COOH was confirmed, but the absorption of amide groups and the like was not clear.

本凝集活性物質はグルコース、ガラクトース等を主構成
成分とする有機酸を含有した高分子量の物質と推定され
る。
This aggregation active substance is estimated to be a high molecular weight substance containing an organic acid whose main constituents are glucose, galactose, etc.

培養液から精製分離した凝集活性物質の粘度試料濃度
相対粘度(c p)センチポイズgAOOml!yel
(30℃, pH6.5 )0.01 1.
620 0.0 5 2.2 0 0 }酸性、アルカリ
性で0.10 5.200 粘度に変化なし溶
媒 i.o o o 試料濃度 相対粘度 (CP)センチポイズg/100
7727! yel 30℃ 55℃ 0.01 1,620 1. 6 toO
.05 2.200 2, 1 000.
10 5,200 5. 1 00精製分
離した凝集活性物質の元素分析 H 6.52係 C 41.04 N O.14 0 51.74 Ash O.56 (吸湿性■) 分子量 100以上(推定) 定性反応 アンスロン反応 ■ カルバゾール反応■ ピューレット反応■ ニンヒドリン反応 e 精製分離した凝集活性物質の溶解性 溶 媒 溶解性 冷、温水に可溶 水 (濃度lチ以上になると 難溶) エチルアルコール 不 溶 エタノール 〃 アセトン 〃 四塩化炭素 〃 ブタノール 〃 エーテル 〃 エチルアルコールに対する溶解性 濃度(アルコール)チ 40%以下 可溶 40〜45チ 不溶、卵白状になる。
Viscosity sample concentration of aggregating active substance purified and separated from culture solution
Relative viscosity (c p) centipoise gAOOml! Yell
(30°C, pH6.5) 0.01 1.
620 0.0 5 2.2 0 0 }0.10 5.200 No change in viscosity in acidic and alkaline solvents i. o o o Sample concentration Relative viscosity (CP) centipoise g/100
7727! yel 30℃ 55℃ 0.01 1,620 1. 6 to O
.. 05 2.200 2, 1 000.
10 5,200 5. 1 00 Elemental analysis of purified and separated agglomerated active substances H 6.52 Section C 41.04 NO. 14 0 51.74 Ash O. 56 (hygroscopicity ■) Molecular weight 100 or more (estimated) Qualitative reaction Anthrone reaction ■ Carbazole reaction ■ Puret reaction ■ Ninhydrin reaction Ethyl alcohol Insoluble Ethanol Acetone Carbon tetrachloride Butanol Ether Solubility in ethyl alcohol (alcohol) 40% or less Soluble 40-45% Insoluble, becomes albumen-like.

保水性大 45係以上 卵白状又は膜状(コロヂオン膜)になる
が攪拌すると 綿状の凝集物となる。
Water retention: 45 or higher It becomes albumen-like or film-like (collodion film), but when agitated, it becomes a flocculent aggregate.

精製分離した凝集活性物質の 臭気 無臭 味 無未 吸湿性 弱い(常温) 色 灰褐色の繊維状物質 本物質(凝集活性物質)の稀薄溶液(濃度1〜100p
pm)にCa++. A7 −−−I Mgs Z n
9Pd等の二価又は三価の無機イオン又は重金属イオ
ンを添加(等量又はその1710以下)すると本物質が
完全に凝集して繊維状となる。
Odor of purified and separated flocculating active substance Odorless taste Non-hygroscopicity Weak (room temperature) Color Grayish brown fibrous substance Dilute solution of the substance (agglomerating active substance) (concentration 1-100p)
pm) and Ca++. A7 ---I Mgs Z n
When divalent or trivalent inorganic ions such as 9Pd or heavy metal ions are added (in an equal amount or 1710 or less), this substance completely aggregates and becomes fibrous.

この無機イオンとの反応は定量的である。This reaction with inorganic ions is quantitative.

実施例 1 精糖工業排水(微粒活性炭含有排水)の処
理試験結果 無処理微粒活性炭素含有水の分析値 pH10.5 透過率T係(83)S
S . 40 p pm〜5 0 p pm 見掛
色度(黒色)平均粒径320mesh以下 精糖工場排水(粒状炭素再生洗滌水)中の微粒炭素は通
常長時間静置しても( 2 4 hr〜48hr)ほと
んど炭素は沈降せず排液は黒色を呈している。
Example 1 Treatment test results of sugar refining industrial wastewater (wastewater containing fine activated carbon) Analysis value of untreated fine activated carbon containing water pH 10.5 Transmittance T factor (83) S
S. 40 ppm to 50 ppm Apparent color (black) Average particle size 320 mesh or less Fine carbon in sugar refinery wastewater (granular carbon regeneration washing water) usually remains undisturbed for a long time (24 hr to 48 hr) Almost no carbon settles and the drained liquid is black in color.

この排液に本微生物凝集剤を1〜3ppm添加し、pH
を7前後に調整し硫酸アノベニウムklppm添加する
と、瞬時に炭素がフロックを形成してそのフロックは沈
降し、排液は蒸留水に準ずる透明な液となる事が判明し
た。
1 to 3 ppm of this microbial flocculant was added to this waste liquid, and the pH
It was found that when the temperature was adjusted to around 7 and klppm of anobenium sulfate was added, carbon instantly formed flocs, the flocs settled, and the drained liquid became a transparent liquid similar to distilled water.

第1表はその試験結果を示した表である。Table 1 shows the test results.

本微生物凝集剤は活性炭素の微粒子の様な不溶性懸濁物
質をpH7前後で硫酸アルミニウムと併用する事によシ
完全に凝集させる事が出来る。
This microbial flocculant can completely flocculate insoluble suspended matter such as fine particles of activated carbon by using it together with aluminum sulfate at around pH 7.

特■黄に懸濁物質の濃度が非常に稀薄(例えば数pI)
m)でも凝集させる事が可能である。
Especially when the concentration of suspended solids in yellow is very dilute (for example, several pI)
m) can also be aggregated.

実施例 2 パルプ排液・K社・Kp排液の処理試験結
果 パルプ排液(Kp排液)を1/lOに稀釈し、pHを6
.0に調整して実験サンプルとした。
Example 2 Treatment test results of pulp waste liquid, K company, Kp waste liquid Pulp waste liquid (Kp waste liquid) was diluted to 1/1O, and the pH was adjusted to 6.
.. It was adjusted to 0 and used as an experimental sample.

パルプのKp排液を1710に稀釈し、本微生物凝集剤
を加え攪拌後硫酸アルミニウムを添加すると、可溶性物
質が多量フロックとなシ上澄液が透明となる。
When the pulp Kp waste liquid is diluted to 1710, the microbial flocculant is added thereto, and aluminum sulfate is added after stirring, a large amount of soluble substances become flocs and the supernatant liquid becomes transparent.

フロック形成と形成フロックの沈降は数分で終了する。Floc formation and sedimentation of the formed flocs are completed in a few minutes.

本凝集剤をパルプ排液に使用する際にはpHを中性に調
整し1/10程度に稀釈して使用する。
When this flocculant is used for pulp drainage, the pH is adjusted to neutral and the coagulant is diluted to about 1/10.

本凝集剤使用によるパルプ排液の効果は脱色と可溶性物
質の不溶化が判に著しい事である。
The effects of pulp drainage using this flocculant are remarkable in decolorization and insolubilization of soluble substances.

形成したフロックのE過性は非常に良へその結果を第2
表に示した。
The E-transactivity of the formed flocs is very good and the result is second to none.
Shown in the table.

実施例 3 製麺排水の処理試験結果 製麺排水 pH6.0 C.0.D5667ppm S.8 4100ppm 凝集剤6〜9ppm,硫酸アルミニウム2ppmを使用
した結果、製麺排水に本微生物凝集剤を添加するとpH
6〜7でC.O.Dが80%除去出来、更に透過率が8
9〜88%になる。
Example 3 Treatment test results of noodle production wastewater Noodle production wastewater pH 6.0 C. 0. D5667ppm S. 8 4100ppm As a result of using flocculant 6-9ppm and aluminum sulfate 2ppm, when this microbial flocculant was added to noodle production wastewater, the pH
C.6-7. O. 80% of D can be removed and the transmittance is 8.
It becomes 9-88%.

凝集は数分でよく凝集物質のE過性は非常に良い事が判
明した。
It was found that the flocculation took only a few minutes and the E-transitivity of the flocculated material was very good.

通常製麺排水の排水処理は非常に困難であり、処理方法
は確立されていない。
Normally, it is very difficult to treat wastewater from noodle production, and no treatment method has been established.

本微生物凝集剤を数ppm添加する事により製麺排水の
水質な著しく向上させる事が出来る。
By adding several ppm of this microbial flocculant, the water quality of noodle production wastewater can be significantly improved.

製麺排水のC.O.D,S.Sの濃度が高い場合は2,
0 0 0 ppm程度に稀釈して本凝集剤な添加して
処理すると良へその結果を第3表に示した。
C. of noodle-making wastewater. O. D.S. 2 if the concentration of S is high;
When the flocculant was diluted to about 0 0 0 ppm and treated, the results were shown in Table 3.

実施例 4 製餡排水の処理試験結果 製餡排水 pH6.2 C.0.D 5750pp
m赤色 S.S L680ppm 製餡排水の場合、排水のpHtcaOで10〜12に調
整した後、本微生物凝集剤を2ppm添加するとC.0
.Dが70係除去出来る。
Example 4 Treatment test results for bean paste manufacturing wastewater.Bean paste manufacturing wastewater pH6.2C. 0. D 5750pp
m red S. S L680ppm In the case of bean paste manufacturing wastewater, after adjusting the pH of the wastewater to 10 to 12 with tcaO, adding 2ppm of this microbial flocculant will cause C.I. 0
.. D can remove 70 units.

それら■給の結果を第4表に示した。Table 4 shows the results of these payments.

形成されるフロックの沈降性は非常によい。The sedimentation properties of the flocs formed are very good.

排水のpH6〜8で硫酸アルミニウムとの併用では脱色
性、C.0.D除去率は悪い。
When used in combination with aluminum sulfate at pH 6-8 of wastewater, C.I. 0. D removal rate is poor.

実施例 5 養豚尿排水の処理試験結果 養豚尿排水に本微生物凝集剤を添加し硫酸アルミニウム
?加えると白色の綿状フロックが瞬時に形成され、その
フロックの沈降性は非常によく、上澄液は透明となり、
その透過率は99.0%になる。
Example 5 Treatment test results for pig urine wastewater When this microbial flocculant was added to pig urine wastewater, aluminum sulfate was removed. When added, white flocculent flocs are instantly formed, and the flocs have very good sedimentation properties, and the supernatant liquid becomes transparent.
Its transmittance will be 99.0%.

又脱色率95.0%で同時にC.0.Dが40%除去出
来、沈降したフロックのE過は非常に良い。
In addition, the decolorization rate is 95.0% and C. 0. 40% of D can be removed, and the E filtration of the settled flocs is very good.

沈降フロック量は豚尿排水100−に対して0.1〜0
.04%である。
The amount of settled floc is 0.1 to 0 per 100 - of pig urine wastewater.
.. It is 04%.

通常養豚尿排水処理は活性汚泥処理等種々実施されてい
るが、処理液の色価、C.O.D、濁度等に多くの問題
があり、いまだ解決されていない。
Normally, pig urine wastewater treatment is carried out in various ways, such as activated sludge treatment, but the color value of the treated liquid, C. O. D. There are many problems with turbidity, etc., which have not been solved yet.

本微生物による凝集活性物質な添加して処理すると、透
過率、脱色率が非常に向上し、又C.0.Dも除去され
る為に養豚尿排水処理の問題が解決されるど同時にその
処理が合理化できる。
When treated with the addition of a flocculating active substance by this microorganism, the transmittance and decolorization rate are greatly improved, and C. 0. Since D is also removed, the problem of treating pig urine wastewater is solved and at the same time the treatment can be streamlined.

それらの結果を第5表及び第6表に示した。The results are shown in Tables 5 and 6.

実施例 6 養豚尿排水を光合成細菌処理した処理液の
菌体スラツヂの凝集処理試験 結果 養豚尿等の畜産排水を特公昭42−11979号記載の
光合成細菌で処理する畜産排水処理が行われているが、
処理液から菌体スラツヂを沈降分離する事が非常に困難
でありその解決が望まれている。
Example 6 Results of flocculation treatment test of microbial sludge obtained by treating pig urine wastewater with photosynthetic bacteria. Livestock wastewater treatment such as pig urine is treated with photosynthetic bacteria as described in Japanese Patent Publication No. 11979/1979. but,
It is extremely difficult to separate bacterial cell sludge from the treated solution by sedimentation, and a solution to this problem is desired.

本微生物凝集活性物質と硫酸アルミニウムを併用すると
その分離が非常に早く完全に行わ法同時にその上澄液の
色価又は透過率が良くなる。
When this microorganism agglutinating active substance is used in combination with aluminum sulfate, the separation is very quick and complete, and at the same time, the color value or transmittance of the supernatant liquid is improved.

その結果を光合成細菌処理液について実施し、その効果
の優れていることが認められた。
The results were conducted on the photosynthetic bacteria treatment solution, and it was found that the effect was excellent.

上澄液のT%(透過率)99〜99.5%,脱色率50
%以上で見掛は無色透明の水と同様になる事が判明した
Supernatant T% (transmittance) 99-99.5%, decolorization rate 50
% or higher, the appearance becomes similar to colorless and transparent water.

上記結果から、微生物を含む液体又は排水、特に細菌の
場合には本凝集活性物質はその効果が著しい事を見出し
、沈降分離の排水処理に有利に利用出来ることが判る。
From the above results, it has been found that the present flocculating active substance has a remarkable effect on liquids or wastewater containing microorganisms, especially bacteria, and it can be seen that it can be advantageously used in wastewater treatment by sedimentation separation.

Claims (1)

【特許請求の範囲】 1 黒色菌科(Dematiaceae)のデマチュー
ム(Dematium)属に属する凝集活性物質産生菌
を培養して得られる凝集活性物質を有効成分とする凝集
剤?各種廃排水に添加して凝集沈降処理を施すことな特
徴とする廃排水の凝集処理方法。 2 凝集活性物質を有効成分とする凝集剤がアルミニウ
ム化合物と併用される特許請求の範囲第1項記載の廃排
水の凝集処理方法。 3 各種廃排水にアルカリ性の状態で凝集活性物質を有
効成分とする凝集剤がカルシウムイオンと併用される特
許請求の範囲第1項又は第2項記載の廃排水の凝集処理
方法。
[Scope of Claims] 1. A flocculant containing as an active ingredient a flocculating active substance obtained by culturing a flocculating active substance producing bacterium belonging to the genus Dematium of the family Dematiaceae? A method for coagulating wastewater treatment characterized by adding it to various wastewaters and performing coagulation sedimentation treatment. 2. The method for flocculating wastewater according to claim 1, wherein a flocculant containing a flocculating active substance as an active ingredient is used in combination with an aluminum compound. 3. A method for coagulating wastewater according to claim 1 or 2, in which a flocculant containing a flocculating active substance as an active ingredient is used in combination with calcium ions in an alkaline state for various wastewaters.
JP10015078A 1977-10-11 1978-08-17 Wastewater coagulation treatment method Expired JPS597518B2 (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
JP10015078A JPS597518B2 (en) 1978-08-17 1978-08-17 Wastewater coagulation treatment method
US05/948,227 US4258132A (en) 1977-10-11 1978-10-03 Process for producing an agglutinating substance utilizing dematium ATCC 20524
DE2844311A DE2844311A1 (en) 1977-10-11 1978-10-11 METHOD FOR MANUFACTURING AN AGGLUTINATING SUBSTANCE AND THE USE OF IT
FR7829017A FR2424959A1 (en) 1977-10-11 1978-10-11 PROCESS FOR THE PRODUCTION OF AN AGGLUTINANT SUBSTANCE BY CULTURE OF A MICRO-ORGANISM AND ITS USE

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10015078A JPS597518B2 (en) 1978-08-17 1978-08-17 Wastewater coagulation treatment method

Related Child Applications (1)

Application Number Title Priority Date Filing Date
JP15591583A Division JPS59213493A (en) 1983-08-26 1983-08-26 Treatment of water

Publications (2)

Publication Number Publication Date
JPS5456241A JPS5456241A (en) 1979-05-07
JPS597518B2 true JPS597518B2 (en) 1984-02-18

Family

ID=14266283

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10015078A Expired JPS597518B2 (en) 1977-10-11 1978-08-17 Wastewater coagulation treatment method

Country Status (1)

Country Link
JP (1) JPS597518B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10113675A (en) * 1996-10-09 1998-05-06 Kokichi Sakai Trapping agent for heavy metal and trapping method of heavy metal
JPH10113677A (en) * 1996-10-09 1998-05-06 Kokichi Sakai Trapping agent for heavy metal and trapping method of heavy metal

Also Published As

Publication number Publication date
JPS5456241A (en) 1979-05-07

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