JPS5985287A - Novel microorganism - Google Patents

Novel microorganism

Info

Publication number
JPS5985287A
JPS5985287A JP57195373A JP19537382A JPS5985287A JP S5985287 A JPS5985287 A JP S5985287A JP 57195373 A JP57195373 A JP 57195373A JP 19537382 A JP19537382 A JP 19537382A JP S5985287 A JPS5985287 A JP S5985287A
Authority
JP
Japan
Prior art keywords
yeast
microorganism
activated sludge
cells
microorganisms
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.)
Granted
Application number
JP57195373A
Other languages
Japanese (ja)
Other versions
JPS6017509B2 (en
Inventor
Makoto Tadenuma
蓼沼 誠
Kazuo Saito
斎藤 和夫
Tetsuo Hasuo
徹夫 蓮尾
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.)
TAX ADM AGENCY
Original Assignee
TAX ADM AGENCY
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 TAX ADM AGENCY filed Critical TAX ADM AGENCY
Priority to JP57195373A priority Critical patent/JPS6017509B2/en
Publication of JPS5985287A publication Critical patent/JPS5985287A/en
Publication of JPS6017509B2 publication Critical patent/JPS6017509B2/en
Expired legal-status Critical Current

Links

Landscapes

  • Enzymes And Modification Thereof (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)

Abstract

PURPOSE:A novel yeast lytic microorganism YLM-1 capable of growing on live yeast cells as a sole carbon source and nitrogen source. CONSTITUTION:A yeast lytic microorganism YLM-1 (FERM-P No.6781) strain capable of growing on live yeast cells, e.g. Endomyces geotrichum IFO 9541 or Saccharomyces cerevisiae IFO 0203, isolated from an activated sludge in the Brewery Research Institute of the National Tax Administrative Agency as a sole carbon source and nitrogen source. The strain has the following characteristics; (1) Gram-negative. (2) cellular form; bacillus. (3) Motility. (4) Aerobe. (5) Capable of growing on live yeast cells as a sole carbon source and nitrogen source.

Description

【発明の詳細な説明】 本発明は、新規微生物に関するものである。[Detailed description of the invention] The present invention relates to a novel microorganism.

本発明の新規微生物YLM−/は、酵母の生菌体を単一
の炭素源及び窒素源と1〜て増殖することが特徴的であ
る。
The novel microorganism YLM-/ of the present invention is characterized in that it grows using live yeast cells as a single carbon source and nitrogen source.

近年、遺伝子操作や細胞融合の際の酵母のプロトプラス
ドグ)調製及び酵母の細胞壁の構造の研究等に使用する
目的で、酵母溶解微生物の検索が精力的に行われている
In recent years, efforts have been made to search for yeast-lytic microorganisms for the purpose of preparing yeast protoplast dogs for genetic manipulation and cell fusion, and for use in studying the structure of yeast cell walls.

発明者らは、高濃度の食品製造廃水を酵母により処理し
た後、活性汚泥等の生物処理を行う新1〜い廃水処理方
式〔吉沢:農化、JJ、7θj〜7// (ypg/)
”Jにおいて、酵母槽で増殖した酵母が活性汚泥槽で、
どのように消えていくか調査を行うため、酵母溶解微生
物用培地を開発12、その培地を用いて酵母処理を実施
1−でいる活性汚泥槽中の酵母溶解微生物の検索を行っ
た結果、国税庁醗造試験所の活性汚泥中から酵旬の生菌
体を牢−の炭素源及び窒素源と;−で増殖する新規微生
物YLM−/(以下[本微生物−1と配す。)を分離1
〜、微工研菌寄第1.7g1号として寄託1〜、本発明
を完成するに至つ/く−8 従来から、酵母細胞壁を溶解する微生物に関する報告は
多数ある〔船津、鶴編「溶菌酵素」〕が、それらの微生
物は、菌体外へ細胞壁溶MNf素を分泌することにより
、加熱処理を行った酵母の死角体のみ、あるいは死菌体
と生菌体の両者を溶解L、通常の肉汁培地、酵母エキス
及び/又はペプトンを含む培地等でも容易に増殖する。
The inventors have developed a new wastewater treatment method [Yoshizawa: Noka, JJ, 7θj~7// (ypg/)] in which highly concentrated food manufacturing wastewater is treated with yeast and then subjected to biological treatment such as activated sludge.
``In J, the yeast grown in the yeast tank is grown in the activated sludge tank,
In order to investigate how yeast-dissolving microorganisms disappear, a culture medium for yeast-dissolving microorganisms was developed12, and yeast treatment was carried out using the medium1-As a result of searching for yeast-dissolving microorganisms in activated sludge tanks, the National Tax Agency Isolation of a new microorganism YLM-/ (hereinafter referred to as [this microorganism-1]) that grows in the carbon and nitrogen sources of fermentation from the activated sludge of the brewing laboratory.
~, Deposited as Fiber Science and Technology Research Institute No. 1.7g1 1~, The present invention was completed/8 There have been many reports on microorganisms that lyse yeast cell walls [Funatsu and Tsuru eds. These microorganisms secrete cell wall-soluble MNf to the outside of the cells, thereby lysing only dead cells or both dead and viable cells of the heat-treated yeast. It grows easily in meat juice medium, medium containing yeast extract and/or peptone, etc.

本微生物は、その形態は通常の細菌に類似(−ているも
のの酵母の死菌体を溶解せず、生菌体のみを溶Ml、、
その溶解法も既知の微生物のような酵母細胞壁溶解酵素
を菌体外へ分泌せず、酵母の生菌体に本微生物が付着し
た状態で酵母の溶解を起′ずとともに増殖すること、さ
らに通常の肉汁培地、酵母エキス及び/又はペプトン等
を含む培地等では増殖しないこと等、極めて特異的な微
生物である。
Although the morphology of this microorganism is similar to that of ordinary bacteria, it does not lyse dead yeast cells and only lyses live cells.
The lysis method is also that unlike known microorganisms, yeast cell wall lytic enzymes are not secreted outside the bacterial cells, and the microorganism grows while attached to viable yeast cells without causing yeast lysis. It is a very specific microorganism, as it does not grow in meat juice medium, medium containing yeast extract and/or peptone, etc.

本発明により、酵母溶解酵素の精製操作のような複雑な
手段を用いることなく、酵母懸濁液に本微生物を直接接
種し、好気的環境下に培養することにより、酵母の生菌
体を溶解することができ、さらにその培養液から酵母エ
キスを効率的に製造することができる。また、食品製造
廃水の酵母処理により増殖1〜だ酵母菌体を本微生物に
より溶解1〜、活性汚泥槽における廃水処Jq+を容易
にするこ本微生物は、下記の菌学的性質を示ず8(形態
的所見〕 ■ 細胞の形及び大きさ°かん(イν)菌03〜0グミ
クロン×0.9〜/9gミクロン■ 運動性:あシ ■ べん(鞭)毛の着生状態;一本のべん(鞭)毛を有
す。
According to the present invention, viable yeast cells can be obtained by directly inoculating the present microorganism into a yeast suspension and culturing it in an aerobic environment without using complicated means such as purifying yeast lytic enzymes. It can be dissolved, and yeast extract can be efficiently produced from the culture solution. In addition, yeast cells that proliferate through yeast treatment of food manufacturing wastewater are dissolved by this microorganism, and this microorganism facilitates wastewater treatment in activated sludge tanks.This microorganism does not exhibit the following mycological properties.8 (Morphological findings) ■Cell shape and size: 03-0 g microns x 0.9-/9 g microns■ Motility: Reeds■ Epiphytic status of flagella: 1 It has a book flagellum.

■ ダラム染色性:陰性 (生育状態) ■ 肉汁寒天斜面培地に酵母ハンセヌラ・アノマラ(H
ansenula anomala )と本微生物を同
時に塗抹培養:白色不透明な酵母の生育帯の中心にパフ
色半透明な本微生物の生育帯を牛しる。
■ Durham staining: negative (growth condition) ■ Yeast Hansenula anomala (H
Ansenula anomala) and the present microorganism are simultaneously smear-cultured: A puff-colored, translucent growth zone of the present microorganism is marked in the center of the white, opaque growth zone of the yeast.

■ 肉汁寒天培地:生育せず。■ Meat juice agar medium: No growth.

■ プロテオーズ・ペグトン(ティフコ社製)O!係、
酵fFJ:エキス0/%、寒天培地:生育せず。
■ Proteose Pegton (manufactured by Tifco) O! Person in charge,
Ferment fFJ: extract 0/%, agar medium: no growth.

■ 肉:r−# ス0.3%、トリプトン製)05%、
D−グルコース07%、寒天培地:生育せず。
■ Meat: r-#su 0.3%, tryptone) 05%,
D-glucose 07%, agar medium: No growth.

■ トリプテイカーゼ・ソイ・ブロス(BB”L社製)
寒天培地:生育せず。
■ Tryptecase soy broth (manufactured by BB”L)
Agar medium: No growth.

■ カシトンO..ff%、酵母エキス、グリセリン0
5%、寒天培地:生育せず。
■ Kasiton O. .. ff%, yeast extract, glycerin 0
5%, agar medium: no growth.

(生理学的性a) Cl)  カタラーセ活性:+ ■ 酸素に対する態度:好気性 (■ 生育pH : pH6〜/θ ■ 生育温度:/2.J”C〜3j℃ (酵母生菌体の溶解) ■ 本微生物により溶解される酵母(溶解と同時に本微
生物が生育する。)の代表例を下記に示す。
(Physiological properties a) Cl) Catalase activity: + ■ Attitude towards oxygen: Aerobic (■ Growth pH: pH 6~/θ ■ Growth temperature: /2.J”C~3J℃ (lysis of viable yeast cells) ■ Representative examples of yeast that are lysed by the present microorganism (the present microorganism grows at the same time as lysis) are shown below.

エンドミセス・ゲオトリクム ( EndorITyces geotrichum)
 工F O  9 3グ/サツカロミセス・セレビシェ ( E+accharomyces cerevisi
aθ)IFO  0,!θ3ンユワニオミセス・オキシ
デンタリス ( Schwanniomycee o(:ciden
talis )1FO /gll/テハリオミセス・ハ
ンセニイ ( ])ebaryomyces hanseni.i
 ) I F 0  0 0 3 +2ピヒア・メンプ
ランファソエンス ( Pichj.a membranaefacien
q ) I F O  θ/62gハンゼヌラ・ムラキ
− ( Hansenu−’La murakji > I
 F O  8g97シテロミセス・マトリテンシス (  Citeromyces  matrjJens
js )I  F  O   0  9  3  yク
リペロミセス拳うクデイス ( Kluyveromyces 1act.is )
工FO  /.:p67デツケラ・インターメディア ( Dekkera intermeclia ) I
 F○ /ぶ9/ザツカロミコプシス・フィブリケラ (、 Saccharo]1ycopeis 1’il
+u]igera ) 7 F O θ/θ3リポミセ
ス・スターギイ ( Lipomy(:ee Starkeyj. ) 
’L P’ 0  / 、2 g 9ハンゼニアスボラ
・バルビエンシス (  HarlSenlaJ’lpOra  valb
yensコs )   I  F  O    θ 乙
 g 3トルロプシス・キャンディダ (  ’I’orulopeis  candida.
  )   ■ F  Cl     θ 乙 。? 
3ブレタノミ七ス・インターメディウス (Brettanomyces intermediu
s )IFO/ 3;f 7キヤンデイダ・クルセイ (Candicla krueei ) I F O/
 395トリコスボロ゛/・ファーメンタンス (Trichosporon fermentans 
) I FO//99■ 本微生物により溶解されない
酵fl(不微生物の生育も起らない。)の代表例を、下
記に示す凸 シゾサツカロミセス畳ボンベ (Schizosaccharomyces pomb
e ) IFOθ3クツスポロボロミセス・ザーモニカ
ラー (5porob○1cmyces salmonico
lor)IFO/θdgクリプトコツカス・アルビダス (cr’yptococcus albidue ) 
I F Oθ3’7gトリコスポロン・ククネウム (Trj、chosporon cutaneum )
工FO//9gロドトルラ拳ルブラ (Rhodotoru]−a、 rubra ) I 
’F○ θに7θロドスポリデイウム・トルロイデス (Rhodosporidium toruloj、d
es ) I F Oθ5Sンロイコスポリデイウム・
スコツティ (Leucoeporidi+im 5COttii 
) I F O/ 、、77ノ本微生物は、酵母処理を
行っている国税庁醸造試験所の活性汚泥から特定の単離
操作によって単離された。すなわち、活性汚泥を殺菌生
理的食塩水で、適宜希釈17、その5θμl と酵母生
菌体懸濁液;1rneを使用直前に溶か1〜.95℃に
保っである下記寒天培地/8’rrteに手早く加え、
よく混合した後、殺菌済ぺ) lJ皿に流i〜込んで固
めた。寒天が、よく同寸ってから36℃でノ日〜5日間
培養した。
EndorITyces geotrichum
E+accharomyces cerevisi (E+accharomyces cerevisi)
aθ) IFO 0,! θ3 Schwanniomyce o(:ciden
talis ) 1FO /gll/ ebaryomyces hansenii ( ) ebaryomyces hanseni. i
) I F 0 0 0 3 +2 Pichj.a membranaefaciens
q) I F O θ/62g Hansenu-'La murakji > I
F O 8g97Citeromyces matrjJens
js ) I F O 0 9 3 y Kluyveromyces 1act.is
Engineering FO/. :p67 Dekkera intermelia I
F○ /bu9/Saccharo]1ycopeis 1'il
+u]igera) 7 F O θ/θ3 Lipomyces Starkey (:ee Starkeyj.)
'LP' 0/, 2 g 9 HarlSenlaJ'lpOra valb
'I'orulopeis candida.
) ■ F Cl θ Otsu. ?
3 Brettanomyces intermediu
s ) IFO/3; f 7 Candicla krueei IFO/
395 Trichosporon fermentans
) I FO//99 ■ A typical example of yeast fl that is not dissolved by this microorganism (no non-microbial growth occurs) is the convex Schizosaccharomyces pombe shown below.
e) IFOθ3cmyces salmonico
lor) IFO/θdgcr'yptococcus albidue
I F Oθ3'7g Trichosporon cutaneum (Trj, chosporon cutaneum)
Engineering FO//9g Rhodotoru Fist Rubra (Rhodotoru]-a, rubra) I
'F○ θ to 7θ Rhodosporidium toruloides (Rhodosporidium toruloj, d
es ) I F Oθ5S nleucosporidium
Leucoeporidi+im 5COttii
) IFO/, 77 microorganisms were isolated by a specific isolation procedure from activated sludge at the National Tax Agency's Brewing Research Laboratory, where yeast treatment is carried out. That is, the activated sludge was appropriately diluted with sterilized physiological saline, and 5θ μl of the diluted solution and 1 rne of live yeast cell suspension were dissolved immediately before use. Quickly add to the following agar medium/8'rrte kept at 95℃,
After mixing well, the mixture was poured into a sterilized dish and solidified. After the agar was made to the same size, it was cultured at 36°C for 5 days.

本機生物分離用寒天培地組成(全容7θme)活性汚泥
抽出液   3θme ′/15リン酸緩衝液(pH7θ)  5θmepH調
整(水酸化ナトリウム溶液)  pH2θ寒天(ディコ
ツ社バクトアガー)  θ72(寒天培地は、/)θ℃
/θ分間殺菌を行った。)なお、酵母生菌体懸濁液I′
i酵匂ノ・ンゼヌラ・アノマラ(Hansenula、
 a、nomala、)Y−/(微工研菌寄第3Sンタ
号)をYM培地(グルコースを係、酵母エキスθ3%、
麦芽エキス03%、ペプトンθj%)/θθmlに/白
金耳接種し、56℃で2日間振とり培養1〜だ培養液を
3θθθrpnt /θ分間遠心分離1〜て菌体を集め
、約lθθm、eの殺菌水で1回洗浄1−11qられた
洗浄菌体を約!×/θ9/ meとなるように殺菌水に
懸濁して調製1.た。
Composition of agar medium for biological separation of this machine (total volume 7θme) Activated sludge extract 3θme '/15 phosphate buffer (pH 7θ) 5θme pH adjustment (sodium hydroxide solution) pH 2θ agar (Dicots Bact Agar) θ72 (agar medium is /) θ℃
Sterilization was performed for /θ minutes. ) In addition, live yeast cell suspension I'
Hansenula,
a, normala, )Y-/(Feikoken Bacteria No. 3S) was added to YM medium (containing glucose, yeast extract θ3%,
Malt extract 03%, peptone θj%)/θθml was inoculated with a platinum loop, shaken and cultured at 56°C for 2 days. Approximately 1-11q of washed bacterial cells are washed once with sterilized water! Prepare by suspending in sterilized water so that ×/θ9/me 1. Ta.

また、活性汚泥抽出液は活性汚泥を蒸留水により洗浄し
たものを乾物濃度と1−て/係になるように蒸留水K 
j跡濁し、その/ S mlをqθmll容ブラウンの
破砕ビンに入れ、θtt5〜05 mmのガラスピーズ
q07を加え、ブラウンの細胞破砕機により活性汚泥中
の諸細胞が完全に破砕される”まで処理(約5分を要し
た。)しだ後、破砕液及びガラスピーズに伺着j〜た破
砕活性汚泥を蒸留水で洗いlJ:f L、3.θθθr
ptn /θ分間遠心分11JIP+−だ上澄み液を蒸
留水で全容を、jOmeと1〜て調製した。
In addition, the activated sludge extract is obtained by washing the activated sludge with distilled water.
Put the /S ml into a Braun crushing bottle with a volume of qθml, add glass beads Q07 with a diameter of 5 to 05 mm, and process with a Braun cell crusher until the cells in the activated sludge are completely crushed. (It took about 5 minutes.) After soaking, wash the crushed liquid and the crushed activated sludge that arrived at the glass beads with distilled water.
The total volume of the supernatant obtained by centrifugation at ptn/θ for 11 JIP+- was prepared with distilled water and jOme.

本微生物が生育1〜だ周囲には溶菌前が生じるので、そ
の溶菌前の中心を釣菌し、再度殺菌生理的食塩水で適宜
希釈i〜だものについて、上記培養を溶菌前以外の細菌
コロニーが検出されなくなる寸で繰り返1〜行い、純化
した。
When this microorganism grows, a pre-lytic state occurs around the area, so collect the center of the pre-lytic area, dilute it again with sterilized physiological saline, and add the above culture to the bacterial colonies other than the pre-lytic area. The process was repeated from step 1 until it was no longer detected for purification.

純化1〜た本微生物の保存は、肉汁寒天斜面培地に酵母
ハンセヌラ書アノマラ(Hansenula anom
ala )Y−/(微工研菌寄Bssンq号)と不微生
物を同時に塗抹し、56℃で2日〜3日培養1〜、白色
不透明な酵母の生育帯の中心にパフ色半透明な不微生物
の生育帯を確認I〜て、2℃で保存する方法がよい。
Preservation of this microorganism after purification was carried out using yeast Hansenula anomaloma on a broth agar slant medium.
ala) Y-/(Feikoken Bacteria Bssnq No.) and non-microorganisms were smeared at the same time and cultured at 56°C for 2 to 3 days.Puff-colored translucent in the center of the white opaque yeast growth zone. A good method is to confirm the growth zone of non-microorganisms and store at 2°C.

本微生物を培養するためには酵母の生菌体が必すであり
、前記単離操作において酵母生菌体懸濁液の代りに加熱
殺菌酵母゛懸濁液を使用した場合は本微生物の単離は不
可能である。
In order to culture this microorganism, viable yeast cells are necessary, and if a heat-sterilized yeast suspension is used instead of a live yeast cell suspension in the above isolation procedure, the cells of this microorganism may be isolated. It is impossible to separate.

本微生物の生育に必ずな無機塩は、リン酸塩及びマグネ
シウム塩であるが、好ましくはマグネシウム塩のイ4ゝ
りに活性汚泥抽出液がよい。活性汚泥抽出液の不微生物
の生育に対する効果は、その中に含まれているマグネシ
ウムの他に未知の有佛化合物の生育促進効果による。
Inorganic salts essential for the growth of this microorganism are phosphates and magnesium salts, and activated sludge extract is preferred over magnesium salts. The effect of the activated sludge extract on the growth of non-microorganisms is due to the growth-promoting effect of an unknown Buddha compound in addition to magnesium contained therein.

培地のpl+は6以上、好寸(2くは7〜95とし、培
養温g!、はi、:i、s℃〜、3;’C,好1しくけ
)7℃〜33′l″′で好気的に/日〜q日(固体培地
では、2日〜S日)培養する。
PL+ of the medium is 6 or more, good size (2 or 7 to 95, culture temperature g!, is i, :i, s °C ~, 3;'C, preferably 1) 7 °C to 33'l''' and aerobically for 1 to q days (2 to S days on solid medium).

このようにして培養j〜た本微生物と培養液及び/又は
わずかに残存している酵母を分離する方法と1〜では、
通常の固液分離手段、例えば遠心分離、ろ過、凝集沈殿
、等電沈殿等が使用できるが、最もt1j’i単な方法
と1〜では3.θθθrpm /θ分間の遠心分離によ
り大部分の酵母を残さとして除去できる。目的に応じて
上澄み液を本微生物の懸濁液とj〜て使用できるが、酵
母を完全に除去するためには、その十澄み液をさらに7
.2ミクロン以下、θgミクロン以上の孔径のメンブラ
ンフィルタ−でろ過すれば、そのろ液から酵勾を完全に
除去するととができる。
A method for separating the microorganism thus cultured from the culture solution and/or slightly remaining yeast;
Usual solid-liquid separation means such as centrifugation, filtration, coagulation precipitation, isoelectric precipitation, etc. can be used, but the simplest method and 1 to 3. Most of the yeast can be removed as a residue by centrifugation for θθθrpm/θ minutes. Depending on the purpose, the supernatant liquid can be used as a suspension of this microorganism, but in order to completely remove yeast, the supernatant liquid must be further diluted with
.. By filtering through a membrane filter with a pore size of 2 microns or less and θg microns or more, the fermentation gradient can be completely removed from the filtrate.

上記メンブランフィルタ−によるろ液から本微生物菌体
を得るには、/θθθθry+m 、:L!θ分間の遠
心分離による沈殿物又は05ミクロン以下のメンブラン
フィルタ−によるろ過残さとして菌体を回収する方法が
よい。
To obtain the present microorganism cells from the filtrate through the membrane filter, /θθθθry+m, :L! It is preferable to collect the bacterial cells as a precipitate obtained by centrifugation for θ minutes or as a filtration residue using a membrane filter of 0.5 microns or less.

上記各方法により得られた不微生物の純度は、殺菌生理
的食塩水による適宜希釈液について前記型内[1操作を
行うことにより検定が可能であり、残存酵@は同希釈液
をYM寒天培地に塗布1〜.30℃)日間培養する方法
により、また、操作中の雑菌等の汚染は、同“希釈液を
ブイヨン寒天培f(12に塗 −布し、3θ℃2日〜7
日間培養する方法により、それぞれ検定できる。
The purity of non-microorganisms obtained by each of the above methods can be verified by performing the above-mentioned in-mold operation [1] for an appropriately diluted solution with sterile physiological saline. Apply 1~. The diluted solution was applied to a broth agar plate (12) and incubated at 3θ℃ for 2 to 7 days.
Each can be assayed by culturing for days.

酵母生菌体を用いて不微生物を培養j〜た培養液中には
核酸及びたんばく質を含み、良好な酵母エキスとなる。
The culture solution obtained by culturing non-organic microorganisms using viable yeast cells contains nucleic acids and proteins and becomes a good yeast extract.

また、廃水処理において酵母処理を採用する場合、モデ
ル廃水としてグルコース:ペプトン:酵母をCOD比率
で/θ:/:5の割合で、汚泥負荷θθSグCOD/7
MLSSで活性汚泥処理を行っておれば、酵母は活性汚
泥槽で順調に消化されていくが、酵母がその比率を上回
った場合、活性汚泥中の原生動物等による酵母の捕食作
用が極端に低下j〜、酵母が消化j−きれぬまま放流水
に流出する。このようなときに、本微生物により、いっ
たん酵母菌体を溶解1−た後、活性汚泥に移すと、本微
生物菌体は活性汚泥中の詰機生物の好しく餌)となり、
円滑な廃水処理を行えるようになる。
In addition, when yeast treatment is adopted in wastewater treatment, glucose:peptone:yeast is used as a model wastewater at a COD ratio of /θ:/:5, and the sludge load θθS is combined with COD/7.
If activated sludge treatment is performed with MLSS, yeast will be smoothly digested in the activated sludge tank, but if the yeast exceeds this ratio, the predation effect on yeast by protozoa in the activated sludge will be extremely reduced. The yeast flows into the effluent water undigested. In such a case, if the yeast cells are once dissolved by the present microorganism and then transferred to activated sludge, the present microorganism cells will become food for the filler organisms in the activated sludge.
This will enable smooth wastewater treatment.

次に、本発明の参考例を示す。Next, reference examples of the present invention will be shown.

参考例/ 不微生物を7×/θ7/ff1eになるように7730
モルリン酸緩衝液、硫酸マグネシウム=2ppm、酵母
ハンセヌラ・アノマラ(Hansenula、 ano
mala )y −/ (9:L?iJl菌寄第33タ
グ号)ix10’7tne、p117θの培地100m
gに接種し、坂ロフラスコ中で3θ℃ノ日間振とう培養
した。その結果、酵母菌数dノ×/θ6/m/! (9
に饅溶解)、不微生物しVノ×/θンme  となった
。培養液を/θθθθr7ノm 、!θ分間遠心分離を
行い、その土澄みについて紫外吸光可法〔生物化学実験
研究会編「生物化学実験法」/76ページ〕によシ核酸
を、1越メンブランフィルタ−とアミド・ブラック/θ
Bを用いて〔菅原 潔、副島正美著「蛋白質の定隈法」
/、ff、5−ページ〕たんばく質を定量1〜だ結果、
7/ppm (リボ核酸と;−て)の核酸及び6 S 
ppnt (印判アルブミンと1−で)のたんばく質を
含む酵母エキス〃得られた。
Reference example/ 7730 to make antimicrobials 7×/θ7/ff1e
Molar phosphate buffer, magnesium sulfate = 2 ppm, yeast Hansenula, ano
mala) y −/ (9:L?iJl fungal infection No. 33 tag number) ix10'7tne, p117θ medium 100m
g, and cultured with shaking in a Sakaro flask for 3θ°C. As a result, the number of yeast bacteria was d no x/θ6/m/! (9
(dissolved in steamed rice), became non-microbial and became V no × / θ nme. Culture solution /θθθθr7nom,! Centrifugation was performed for θ minutes, and the resulting soil was filtered using an ultraviolet absorption method [Biochemistry Experimental Research Group, ed. "Biochemistry Experimental Methods", page 76].
Using B [Kyoshi Sugawara, Masami Soejima, “Protein Determination Method”]
/, ff, page 5] As a result of quantifying protein 1~,
7/ppm (ribonucleic acid; -te) of nucleic acids and 6S
A yeast extract containing proteins of ppnt (1- with stamp albumin) was obtained.

参考例ノ 洗米廃水中で3θ℃ノ日間振とう培養1〜だ酵母)S7
ゼヌラ轡アノマラ(Hasenula anoma]、
a ) Y −7(微工研菌寄第3529号)を3.0
00 rptnla分間遠心分離1−て集め、この菌体
に48モルリン酸緩衝液と活性汚泥抽出液を活性汚泥乾
物濃度と1−でXθθθppmとなるように加え、本微
生物を/x/θ77’ trteになるように添加し、
30℃7日間振とり培養1〜だ結果、培養開始時にノ×
/θR7me存在した酵母が培養終了時に/×/θ6/
mlに減少;7、一方、不微生物は、2.、SX/θ’
/ meに増加した。
Reference Example: Shaking culture in rice washing wastewater for 3θ℃ for 1 to 2 days) Yeast) S7
Hasenula anoma,
a) Y-7 (Feikoken Bibori No. 3529) to 3.0
The microorganisms were collected by centrifugation for 1-00 rptnla minutes, and 48M phosphate buffer and activated sludge extract were added to the microorganisms so that the activated sludge dry matter concentration was 1-Xθθθppm, and the microorganisms were adjusted to /x/θ77' trte. Add so that
Shaking culture for 7 days at 30°C. As a result, no
/θR7me existed yeast at the end of culture /×/θ6/
ml; 7, while non-microorganisms are 2. , SX/θ'
/me increased.

この培養液に活性汚泥をM’L S S  と1−て3
、θθθppmとなるように加え1.25℃で1日間通
気した結果、不微生物は、活性汚泥処理前にlθB’/
rat!存在したものが活性汚泥処理後7×/θ6/ 
mQ?に減少j−た。すなわち、洗米廃水中の有機物が
酵母を経て、最終的に活性汚泥中の原生動物等に捕食さ
れやずい本微生物に変換されたことになる。
Add activated sludge to this culture solution with M'LSS.
, θθθppm and aerated at 1.25℃ for 1 day.
rat! What was present was 7×/θ6/ after activated sludge treatment.
mQ? It decreased to . In other words, the organic matter in the rice washing wastewater passed through yeast and was finally preyed on by protozoa in the activated sludge and converted into the microorganisms of Yazumoto.

Claims (1)

【特許請求の範囲】[Claims] (1)下記の菌学的性質を有することを特徴とする新規
微生物YLM−/(微工研菌寄第67g/号)株。 イ グラム陰性 口 細胞の形状はかん(桿)菌 ハ 運動性あり 二 好気性菌 ホ 酵母の生菌体を単−炭素源及び窒素源と1−で増殖
(1) A novel microorganism strain YLM-/ (Feikoken Bacterial Serial No. 67g/) characterized by having the following mycological properties. B. Gram-negative mouth Cell shape is rod-like Bacteria C. Motile B. Aerobic Bacteria E. Propagation of live yeast cells with a single carbon source and a nitrogen source.
JP57195373A 1982-11-09 1982-11-09 new microorganisms Expired JPS6017509B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57195373A JPS6017509B2 (en) 1982-11-09 1982-11-09 new microorganisms

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57195373A JPS6017509B2 (en) 1982-11-09 1982-11-09 new microorganisms

Publications (2)

Publication Number Publication Date
JPS5985287A true JPS5985287A (en) 1984-05-17
JPS6017509B2 JPS6017509B2 (en) 1985-05-02

Family

ID=16340087

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57195373A Expired JPS6017509B2 (en) 1982-11-09 1982-11-09 new microorganisms

Country Status (1)

Country Link
JP (1) JPS6017509B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05246064A (en) * 1992-03-06 1993-09-24 Tdk Corp Thermal head
JPH0649592U (en) * 1992-12-09 1994-07-08 株式会社ホウショウ Vertical shaft drilling equipment

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05246064A (en) * 1992-03-06 1993-09-24 Tdk Corp Thermal head
JPH0649592U (en) * 1992-12-09 1994-07-08 株式会社ホウショウ Vertical shaft drilling equipment

Also Published As

Publication number Publication date
JPS6017509B2 (en) 1985-05-02

Similar Documents

Publication Publication Date Title
EP0531991B1 (en) Method for preparing chitosan
JP3327469B2 (en) Methods for biological inactivation of nucleic acids
CN111378592B (en) Bacillus licheniformis and method for treating malodorous organic wastewater by using same to purify water
JPS5985287A (en) Novel microorganism
US4737461A (en) Novel bacteriolytic enzyme and process for preparing the same
JP3691102B2 (en) Wastewater treatment method
Bae et al. Isolation of bacterial strain antagonistic to Pyricularia oryzae and its mode of antifungal action
CN115786300B (en) Bacillus amyloliquefaciens with low yield and application thereof
JP2964163B2 (en) Method for producing R (-)-1,3-butanediol
NZ221455A (en) Microbial production of cellulose
JPS6221509B2 (en)
JPH09253699A (en) Solubilizing method in biological treatment of sludge
US3558432A (en) Waxolytic enzyme preparation
CN117568235A (en) Bacillus subtilis for producing nitrite oxidoreductase and application thereof
Olasupo et al. A comparative study of industrial and local yeast isolates
Patil et al. Top and bottom yeasts together accelerate ethanol production in molasses fermentation
JPS6075283A (en) Novel bacterial strain
JPS59179065A (en) Novel microorganism
JPS6279782A (en) Heat-resistant lipase
JPH04299980A (en) High-density culture of bacterial belonging to genus thiobacillus
JPH04158784A (en) Production of yeast cell wall-lysing enzyme and its utilization
JPH04287685A (en) Collagenase producing bacterium
JPS59232095A (en) Production of phenylacetic acid
JPS61115497A (en) Production of nucleic acid
JPS6135895A (en) Method for controlling and preventing filamentous bulking