JPH09103290A - Noble microorganism capable of deodorization in sewage treatment, its culture medium composition and cultivation - Google Patents

Noble microorganism capable of deodorization in sewage treatment, its culture medium composition and cultivation

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Publication number
JPH09103290A
JPH09103290A JP8115066A JP11506696A JPH09103290A JP H09103290 A JPH09103290 A JP H09103290A JP 8115066 A JP8115066 A JP 8115066A JP 11506696 A JP11506696 A JP 11506696A JP H09103290 A JPH09103290 A JP H09103290A
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Japan
Prior art keywords
microorganism
bacillus subtilis
sewage treatment
kctc
growth
Prior art date
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Application number
JP8115066A
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Japanese (ja)
Inventor
Heijiyun Kiyou
秉準 姜
Kokushin Yasu
國振 安
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ASUULE KK
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ASUULE KK
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    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12NMICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N1/00Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
    • C12N1/20Bacteria; Culture media therefor
    • AHUMAN NECESSITIES
    • A61MEDICAL OR VETERINARY SCIENCE; HYGIENE
    • A61LMETHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
    • A61L9/00Disinfection, sterilisation or deodorisation of air
    • A61L9/01Deodorant compositions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12NMICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N1/00Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
    • C12N1/20Bacteria; Culture media therefor
    • C12N1/205Bacterial isolates
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12RINDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
    • C12R2001/00Microorganisms ; Processes using microorganisms
    • C12R2001/01Bacteria or Actinomycetales ; using bacteria or Actinomycetales
    • C12R2001/07Bacillus
    • C12R2001/125Bacillus subtilis ; Hay bacillus; Grass bacillus

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  • Life Sciences & Earth Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Wood Science & Technology (AREA)
  • Biotechnology (AREA)
  • Bioinformatics & Cheminformatics (AREA)
  • Zoology (AREA)
  • Genetics & Genomics (AREA)
  • Microbiology (AREA)
  • General Health & Medical Sciences (AREA)
  • Biochemistry (AREA)
  • Biomedical Technology (AREA)
  • Virology (AREA)
  • General Engineering & Computer Science (AREA)
  • Tropical Medicine & Parasitology (AREA)
  • Medicinal Chemistry (AREA)
  • Hydrology & Water Resources (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Epidemiology (AREA)
  • Animal Behavior & Ethology (AREA)
  • Public Health (AREA)
  • Veterinary Medicine (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a noble microorganism developing the deodorizing effect in sewage treatment, comprising Bacillus subtilis (KCTC 8662P), utilizable under aerobic conditions, well growable in an aqueous enriched medium containing carbon source and nitrogen source. SOLUTION: This noble microorganism comprises Bacillus subtilis (KCTC 8662P), utilizable under aerobic conditions, well growable in an aqueous enriched culture medium containing carbon source and nitrogen source and developing the deodorizing effect in sewage treatment. This microorganism decomposes sewage to remove foul smell and is useful in sewage treatment. In addition, it can be utilized in fresh water ponds, fish farming, reservoirs, poultry houses, livestock barns, incineration plants, refrigerators, clothe-changing rooms, cars, boats for deodorization. This novel microorganism has been found near the fresh water fish farming ponds or at the pace of dumping ground. Because the places were filled with malodor at the beginning, but 15 days later, it was observed that the malodor dissipated and swage reduced and a strain of a microorganism having excellent deodorizing effect has been isolated.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】下水処理用の脱臭能をもつ微生物
と、その培地組成物及び培養方法に関するもので、より
詳しくは、汚水のカスを分解して悪臭を除去し、下水管
に着いている油脂成分を分解する下水処理と脱臭方法に
関するものである。
[Field of Industrial Application] The present invention relates to a microorganism having a deodorizing ability for treating sewage, a medium composition and a culturing method thereof. More specifically, it decomposes waste water debris to remove a bad odor, and The present invention relates to a sewage treatment and a deodorizing method for decomposing oil and fat components.

【0002】[0002]

【従来の技術】既に開発された下水処理製剤としては、
酵母,ビブリオ菌及び活性汚泥等の多い微生物が知られ
ているが、従来の下水処理菌では、廃水管内に蓄積して
いる汚物のカスを分解できず、脱臭もできないという問
題点があった。生物学的廃水処理場で発生する有機性ス
ラッジも、やはり、濃縮,安定化,改良,脱水,焼却等
の方法で処理しているのが現状で、この処理に要する費
用は高額に及んでいる。
2. Description of the Related Art As already developed sewage treatment preparations,
Although many microorganisms such as yeast, vibrio bacterium, and activated sludge are known, the conventional sewage treatment bacteria have a problem in that they cannot decompose debris accumulated in the wastewater pipe and cannot deodorize. The organic sludge generated at the biological wastewater treatment plant is also treated by the methods such as concentration, stabilization, improvement, dehydration and incineration, and the cost required for this treatment is high. .

【0003】[0003]

【発明が解決しようとする課題】環境保全に関する問題
が、産業の各分野で最近になって検討されてきている
が、下水の汚物カスと悪臭も公害の一種であり、種々の
産業分野で問題になっている。特に、食堂等のサービス
業界においては、悪臭が発生して大きな問題を惹き起こ
しているという件数は、年々増加しているのが実情であ
る。而も、都市の下水は、溶解性,コロイド形態,また
は浮遊固形物のような有機物質になっていて、流出され
た油脂分等の汚物によって排水管が次第に狭まり、最終
的には閉鎖してしまうこともあり、このような場合、下
水処理の問題は解決すべき大きな問題となってきた。
Problems relating to environmental protection have recently been investigated in various fields of industry, but sewage debris and offensive odors are also a type of pollution, and are problematic in various industrial fields. It has become. In particular, in the service industry such as a cafeteria, the number of cases in which a bad odor is generated and causing a big problem is actually increasing year by year. In addition, the sewage of the city is an organic substance such as soluble, colloidal, or suspended solid, and drainage pipes are gradually narrowed by spilled oil and fats, and eventually closed. In such a case, the problem of sewage treatment has become a major problem to be solved.

【0004】本発明の目的は、上述の問題点を解決でき
る下水処理及び脱臭能力をもっている新規の微生物を含
む微生物製剤を提供しようとするものである。
An object of the present invention is to provide a microbial preparation containing a novel microorganism having sewage treatment and deodorizing ability which can solve the above-mentioned problems.

【0005】本発明の他の目的は、上記の微生物を培養
するための培地組成物とこれを利用した培養方法を提供
するものであり、また上記の微生物製剤を利用した下水
処理方法及び脱臭方法をも提供しようとするものであ
る。
Another object of the present invention is to provide a medium composition for culturing the above-mentioned microorganism and a culturing method using the same, and a sewage treatment method and a deodorizing method using the above-mentioned microorganism preparation. Is also intended to be provided.

【0006】[0006]

【課題を解決するための手段】上記の目的を達成するた
めの本発明の微生物製剤は、1995年4月26日付で韓国科
学技術研究院にバチルス・スブチルス菌(KCTC 86
62P)として寄託した。
[Means for Solving the Problems] A microbial preparation of the present invention for achieving the above-mentioned object was obtained from the Bacillus subtilis bacterium (KCTC 86) at the Korea Institute of Science and Technology on April 26, 1995.
62P).

【0007】上記の菌を培養する培地組成物は、蒸留水
1リットルに対して、澱粉8〜15g,ビフイクスラクト
0.5 〜4g ,ペプトン7〜14g 及び塩化ナトリウム2〜
7gで構成される。
The medium composition for cultivating the above-mentioned bacteria is such that the starch is 8 to 15 g, and the bifix tract is added to 1 liter of distilled water.
0.5-4g, peptone 7-14g and sodium chloride 2-
Composed of 7g.

【0008】また培養方法としては、上記の組成物に対
し、上記の微生物を接種した後、25〜32℃の温度範囲及
び6.5 〜8.5 の pH値において培養することで構成され
る。
[0008] As a culture method, the above composition is inoculated with the above microorganisms and then cultured at a temperature range of 25 to 32 ° C and a pH value of 6.5 to 8.5.

【0009】以下本発明の構成を添付の図面を参照し
て、より具体的に述べる。
Hereinafter, the structure of the present invention will be described more specifically with reference to the accompanying drawings.

【0010】本発明は、従来のバチルス・スブチルスが
もっていない下水処理及び脱臭能力を有するバチルス・
スブチルス菌に関するものとして、1995年4月26日付で
韓国科学技術研究院にKCTC 8662Pとして寄託され
た。
The present invention is a Bacillus sulcus which has sewage treatment and deodorizing ability that conventional Bacillus subtilis does not have.
It was deposited as KCTC 8662P at the Korea Institute of Science and Technology on April 26, 1995, regarding Subtilis.

【0011】本発明者らは、下水処理菌や脱臭能力をも
つ菌株を見付けるために努力した結果、淡水魚の養魚場
周辺において、養魚池の底のヘドロを捨ててある所で、
始めは悪臭がひどかったが、約15日後は悪臭がなくな
り、カスの量も減ることに着眼し、その土壌で脱臭効果
が著しい本発明の菌株を分離した。上記の分離菌は、形
態学的,生物学的及び生化学的性状において、バチルス
・スブチルス菌に属するが、汚物のカスの減少能力と脱
臭能力に優れた有用性においては、通常のバチルス・ス
ブチルス菌株には見られなかったものなので、上記の分
離菌は、バチルス・スブチルスの新しい菌株であるもの
と判断された。
As a result of efforts to find a sewage treatment bacterium and a strain having a deodorizing ability, the present inventors have discarded sludge at the bottom of a fish pond in the vicinity of a freshwater fish farm.
The odor was bad at first, but after about 15 days, the odor disappeared and the amount of dregs was reduced, and the strain of the present invention having a remarkable deodorizing effect was isolated in the soil. The above-mentioned isolates belong to Bacillus subtilis morphologically, biologically and biochemically. However, in terms of their usefulness in reducing waste debris and deodorizing ability, they are usually Bacillus subtilis. Since it was not found in the strain, it was judged that the above-mentioned isolated strain is a new strain of Bacillus subtilis.

【0012】本発明に従う菌株の形態学的,生物学的及
び生化学的特性は、以下の通りである。
The morphological, biological and biochemical properties of the strain according to the invention are as follows.

【0013】形態学的特性 上記の菌は、桿菌で、大きさは1.0 〜1.5 ×3.5 〜4.0
μm であり、細胞膜で囲まれており核を持っている。而
も、芽胞を持っているのが特徴的で、隔膜を保有してい
る培養条件が不足する時には、胞子を形成し、菌体自体
は鞭毛も10個ぐらい持っている(図1参照)。
Morphological characteristics The above-mentioned bacterium is a rod-shaped bacterium and has a size of 1.0 to 1.5 x 3.5 to 4.0.
μm, surrounded by the cell membrane and having a nucleus. Moreover, they are characterized by having spores, which form spores when the culture conditions holding the diaphragm are insufficient, and the cells themselves have about 10 flagella (see Fig. 1).

【0014】生物学的特性 上記の菌は運動性があり、生理食塩水に懸濁した状態
で、肉汁寒天平板に接種して、37℃で24時間培養しても
発育が良好であった。
Biological characteristics The above-mentioned bacteria are motile, and even when they were inoculated on a broth agar plate in a state of being suspended in physiological saline and cultured at 37 ° C for 24 hours, the growth was good.

【0015】培地状の集落周縁は、円形ではない荒い形
であり、集落は不透明で、培地の種類によっては白い色
とか薄い黄色味を帯びている。
The peripheral edge of the medium-shaped colony is not circular but rough, and the colony is opaque and has a white or light yellowish tint depending on the type of medium.

【0016】各培地での発育状態は、普通寒天培地,綿
羊血液培地,ハートインピュゾン培地,プレーンハート
インピュゾン培地,トリプチクソイ寒天培地では発育が
良好だが、食塩卵黄寒天培地,ビチビチボル培地及びゾ
ベル2216培地では発育しなかった。
Regarding the growth state in each medium, normal agar medium, cotton sheep blood medium, heart inpuzon medium, plain heart inpuzon medium, trypticosoi agar medium showed good growth, but saline yolk agar medium, Vitibitibor medium and Zover. It did not grow on 2216 medium.

【0017】温度別発育は、図2及び図3より理解され
るように、25℃,30℃及び35℃でよく成長し、 pH6.5
〜8.5 (望ましくは pH6.5 〜7.0 )において発育が良
好であったが、 pH6.0 以下では発育が不良だった。酸
素利用には好気性であり、溶血性はなかった。
As shown in FIGS. 2 and 3, the temperature-dependent growth was well grown at 25 ° C., 30 ° C. and 35 ° C., and the pH was 6.5.
The growth was good at ˜8.5 (preferably pH 6.5 to 7.0), but the growth was poor at pH 6.0 or less. It was aerobic for oxygen utilization and not hemolytic.

【0018】生化学的特性 上記の菌は、グラム陽性であり、ジエル‐ニルソン染色
に赤く染色される抗酸性菌である。また、窒素酸塩を還
元させ、枸櫞酸を利用し、オクシダゼ,カタルラゼ及び
VP反応にも陽性であった。然し、インドルと硫化水素
は生成しなかったし、ウレアゼにも陰性反応を現わし
た。スタチ,エスクリン及びセルロースを加水分解した
が、アルギニンは加水分解できなかった。
Biochemical properties The above-mentioned bacteria are acid-fast bacteria which are Gram-positive and stain red with Dier-Nilsson stain. In addition, nitrate was reduced and oxalic acid was used, and it was also positive for oxidase, catalase and VP reaction. However, neither indol nor hydrogen sulfide was produced, nor did it react negatively with urease. Statin, esculin and cellulose were hydrolyzed but arginine could not be hydrolyzed.

【0019】炭水化物の利用 上記の菌の炭水化物利用能力を検定するために、ペノル
レド液体培地に一定量の炭水化物を入れて基礎培地と
し、上記の菌を接種した。
Utilization of Carbohydrate In order to assay the carbohydrate utilization ability of the above-mentioned bacteria, a certain amount of carbohydrate was added to Penolredo liquid medium as a basal medium, and the above-mentioned bacteria were inoculated.

【0020】上記の菌は、D‐グルコース,D‐フルク
トース及びトレハルロースを分解して酸を生成したが、
L‐アラビノース,D‐キシロース,ラクトース,D‐
ソルリトル,D‐マンニトール及びイノシトルは分解で
きなかった。
The above-mentioned fungus decomposed D-glucose, D-fructose and trehalulose to produce an acid.
L-arabinose, D-xylose, lactose, D-
Sollittle, D-mannitol and inositol could not be decomposed.

【0021】安定性試験 上記の菌の菌体のみをマウスに経口投与した結果では、
半数致死濃度は殆ど無限大で、マウスの表皮塗布試験に
おいても全然反応がなかった。
Stability test As a result of oral administration of only the bacterial cells of the above-mentioned bacteria to mice,
The half-maximal lethal concentration was almost infinite, and there was no reaction in the mouse epidermal application test.

【0022】上記の菌の形態学的,生物学的及び生化学
的特性の測定結果によれば、通常のバチルス・スブチル
ス菌株とは、細胞の大きさ,葡萄糖の醗酵的分解,アル
ギニンの加水分解等一般的な面においては同じだった
が、発育温度(5〜55℃),発育 pH値(5.5 〜8.5 )
と、脱臭及びスラッジ分解能力においては既存のバチル
ス・スブチルスとは差異があった。従って、上記の菌は
バチルス・スブチルスの新しい菌株と判断される。
According to the measurement results of the morphological, biological and biochemical characteristics of the above-mentioned bacteria, the ordinary Bacillus subtilis strain was found to be a cell size, a fermentative decomposition of glucose and a hydrolysis of arginine. Although it was the same in general aspects, growth temperature (5-55 ℃), growth pH value (5.5-8.5)
There was a difference in deodorization and sludge decomposition ability from the existing Bacillus subtilis. Therefore, the above-mentioned bacterium is judged to be a new strain of Bacillus subtilis.

【0023】また、上記の菌を大量培養するための好ま
しい培地組成は、蒸留水1リットルに対して、澱粉8〜
15g 、ビフイクストラクト0.5 〜4g 、ペプトン7〜14
g 及び塩化ナトリウム2〜7g が望ましい。上記の澱粉
が全体培地組成物に対して8g 以下なら発育が不良で、
15g 以上なら栄養が過多供給されて代数増殖期に至るま
で澱粉全体を利用できなかった。而も、上記のビフイク
ストラクトが0.5g以下なら、菌体発育が円滑ではない
し、4g 以上なら菌体の最適発育範囲を越えて過剰投与
となり、ペプトンが7g 以下なら上記の菌の成長が不良
で、14g 以上なら最大発育時間には早く達するが、菌体
の本性が低下する傾向があり、上記の塩化ナトリウムが
2g 以下なら発育が不良で、7g 以上なら本菌自体の最
適な塩分濃度の範囲を超えてしまう。
A preferable medium composition for culturing the above-mentioned bacterium in a large amount is starch 8 to starch per 1 liter of distilled water.
15g, biffix tract 0.5-4g, peptone 7-14
g and 2 to 7 g sodium chloride are preferred. If the above starch is 8 g or less with respect to the whole medium composition, the growth is poor,
If it was more than 15g, the whole starch could not be used until the algebraic growth phase due to excessive nutrient supply. In addition, if the above-mentioned bifix tract is 0.5 g or less, the bacterial growth is not smooth, and if it is 4 g or more, it is overdosed beyond the optimal growth range of the bacterial cells, and if peptone is 7 g or less, the growth of the above bacteria is poor. If the amount is 14 g or more, the maximum growth time will be reached sooner, but the nature of the cells will tend to decline. If the sodium chloride content is 2 g or less, the growth will be poor. It goes beyond the range.

【0024】上記の培地組成物に上記の菌を接種した
後、25〜35℃の温度範囲及び6.5 〜8.5 の pH値で培養
し、大量増殖することができる。
After inoculating the above-mentioned medium composition with the above-mentioned bacteria, it can be cultured in a temperature range of 25 to 35 ° C. and a pH value of 6.5 to 8.5 to mass-proliferate.

【0025】このように増殖した培養物は、多量の菌体
が含まれているので、そのまま下水処理場または浄化槽
に添加することができる。また、培養物を遠心分離して
純粋菌体を得ることができ、滅菌生理食塩水を利用して
洗った後、澱粉等の賦形剤と混ぜたものを微生物製剤と
しても使用し得る。
Since the culture thus grown contains a large amount of cells, it can be added as it is to a sewage treatment plant or a septic tank. Further, the culture can be centrifuged to obtain pure cells, and after washing with sterile physiological saline, a mixture with an excipient such as starch can be used as a microbial preparation.

【0026】以下の実施例を通じて、本発明の効果をよ
り具体的に認め得るが、下記の例は、何れも本発明の範
囲を限定するものではない。
The effects of the present invention can be more specifically recognized through the following examples, but the following examples do not limit the scope of the present invention.

【0027】[0027]

【実施例】実施例1 バチルス・スブチルス菌(KCTC 8662P)の大量培
養の培地組成と、総有機物濃度の減少効果。培地組成
は、澱粉12g ,ビフイクストラクト2g ,ペプトン10g
,塩化ナトリウム4.5gを蒸留水1リットルに溶解した
後、 pH値を7.0 に調整した。このように組成した培地
を500ml のフラスコに入れてバチルス・スブチルス菌
(KCTC8662P)に接種して、35℃で24時間振り動か
して培養した。
[Examples] Example 1 Medium composition of a large-scale culture of Bacillus subtilis (KCTC 8662P) and an effect of reducing total organic matter concentration. The medium composition is 12 g of starch, 2 g of bifix tract, 10 g of peptone.
After dissolving 4.5 g of sodium chloride in 1 liter of distilled water, the pH value was adjusted to 7.0. The medium thus constructed was placed in a 500 ml flask, inoculated with Bacillus subtilis (KCTC8662P), and cultured by shaking at 35 ° C. for 24 hours.

【0028】なお、この培養の際に、本発明の核心であ
るバチルス・スブチルス(KCTC8662P)が好気性菌
であることを考慮して、酸素の供給導入をしてもよい。
導入の方法としては、ポンプ式の供給、または固形酸素
を投入することが実用的である。
During this culture, oxygen may be supplied and introduced considering that Bacillus subtilis (KCTC8662P), which is the core of the present invention, is an aerobic bacterium.
As a method of introduction, it is practical to supply by pump or to supply solid oxygen.

【0029】ここで、得られた培養液を低温遠心分離機
によって、3,000 回転/分で30分間遠心分離し、5g の
菌体を集菌した後、−75℃で凍結乾燥して、その製造粉
末を澱粉200gに混ぜ、総有機物減少試験の微生物製剤と
して使った。
Here, the obtained culture solution was centrifuged at 3,000 rpm for 30 minutes by a low-temperature centrifuge to collect 5 g of bacterial cells, which was then lyophilized at -75 ° C. to produce it. The powder was mixed with 200 g of starch and used as a microbial preparation for the total organic matter reduction test.

【0030】澱粉の製造工場から排出される澱粉の廃液
5トンが入っている沈澱槽に対して、微生物製剤100gを
添加し、経過日数に従う総有機物の濃度を測定した。対
照領域では、本微生物製剤を入れてない沈澱槽の総有機
物濃度も同時に測定して、その結果を図4に示した。図
4から判るように、上記の微生物製剤を入れた沈澱槽の
総有機濃度は、添加3日後78mg/lに急激に減ったが、非
添加領域では145mg/lと添加領域の2倍以上だった。5
日後、添加領域は30mg/lと急激に減ったが、非添加領域
は110mg/l であった。10日後には、添加領域が23mg/lで
あったが、非添加領域では92mg/lであり、15日後には、
添加領域が14mg/l、非添加領域は81mg/lの結果が判っ
た。20日後最終的に測定した結果では、添加領域が11mg
/lであったのに反し、非添加領域は78mg/lであった。
100 g of the microbial preparation was added to a settling tank containing 5 tons of starch waste liquid discharged from the starch manufacturing plant, and the concentration of total organic matter was measured according to the elapsed days. In the control area, the total organic matter concentration in the sedimentation tank containing no microbial preparation was also measured, and the results are shown in FIG. As can be seen from Fig. 4, the total organic concentration in the sedimentation tank containing the above-mentioned microbial preparation decreased sharply to 78 mg / l 3 days after the addition, but it was 145 mg / l in the non-addition area, which was more than double the addition area. It was 5
After a day, the spiked area decreased sharply to 30 mg / l, while the spiked area was 110 mg / l. After 10 days, the added area was 23 mg / l, but in the non-added area it was 92 mg / l, and after 15 days,
The results were found to be 14 mg / l in the added region and 81 mg / l in the non-added region. After 20 days, the final measurement shows that the added area is 11 mg.
In contrast to / l, the non-added area was 78 mg / l.

【0031】上記の結果から、本発明に従う菌株は、少
量でも多くの有機物を分解し、減少させる効果が卓越し
ていることが判った。
From the above results, it was found that the strain according to the present invention has an excellent effect of decomposing and reducing many organic substances even in a small amount.

【0032】実施例2 バチルス・スブチルス菌(KCTC 8662P)の脱臭効
果。 粉末製造法:上記の実施例1の培地から培養した培養物
を菌体の成分が壊れないようにする為に、高速遠心分離
機の温度を10℃に調整して、毎分3,000 回転/分で30分
間遠心分離1回を行なった後、0.85滅菌生理食塩水に集
菌した菌体を遠心分離機にかけ、3,000 回転/分で30分
間3回洗滌する。洗った菌体を5ml用量の凍結乾燥用試
験管に入れて、1分当たり30回転させ、−50℃で予備凍
結した後、−75℃で40分間凍結する。
Example 2 Deodorizing effect of Bacillus subtilis (KCTC 8662P). Powder production method: The temperature of the high-speed centrifuge was adjusted to 10 ° C. and the rotation speed was 3,000 revolutions / minute in order to prevent the components of the cells from destroying the culture that was cultured from the medium of Example 1 above. After centrifuging once for 30 minutes, the cells collected in 0.85 sterilized physiological saline are centrifuged and washed three times for 30 minutes at 3,000 rpm. The washed cells are placed in a 5 ml-dose freeze-drying test tube, rotated 30 minutes per minute, pre-frozen at -50 ° C, and then frozen at -75 ° C for 40 minutes.

【0033】凍結乾燥した菌体は、滅菌した磨砕機で粉
砕し、粉末化する。
The lyophilized cells are pulverized with a sterilized grinder to give a powder.

【0034】液状製造法:上記粉末を細菌2.0 ×106 ce
ll/ml になるように、0.85%滅菌生理食塩水に懸濁し
て、一定の容器に入れて保管する。
Liquid manufacturing method: Bacteria 2.0 × 10 6 ce was prepared from the above powder.
It is suspended in 0.85% sterilized physiological saline so that the concentration becomes ll / ml, and stored in a fixed container.

【0035】脱臭効果:地下空間の10トン用量の貯水槽
に、上記菌株の液状製剤2リットルと、粉末製剤5g を
共に投与して実験した。投与1ケ月後、悪臭濃度を測定
してみた。投与前にポンプで汚水を取上げた時、悪臭濃
度は40,000逆臭(スレッシュホールドー THRESHOLD)で
あったが、投与1ケ月後に、汚水を取上げた時の悪臭濃
度は、2,000 逆臭まで下がった。取上げない状態では、
上記の製剤の投与前悪臭濃度が250 逆臭であったのに投
与1ケ月後には85逆臭しか出なかった。
Deodorizing effect: An experiment was carried out by administering 2 liters of the liquid preparation of the above strain and 5 g of the powder preparation together to a water tank having a dose of 10 tons in the underground space. One month after the administration, the malodor concentration was measured. When the sewage was taken up by the pump before the administration, the malodor concentration was 40,000 reverse odor (threshold THRESHOLD), but one month after the administration, the odor concentration when the sewage was taken dropped to 2,000 reverse odor. When not picked up,
The malodor concentration before administration of the above formulation was 250 reverse odor, but only one reverse odor was produced one month after the administration.

【0036】実施例3 綿に対するバチルス・スブチルス菌(KCTC 8662
P)の吸着法。上記の菌の脱臭効果を利用して、実用的
な製品を製造するために、綿を菌体吸着気質として使用
した。綿を直径1cm、長さ3cmの円筒形に成形し、121
℃で15分間滅菌し、原材料の綿についている雑菌を除去
する。雑菌を除去した円筒形の綿を50℃で無菌状態に乾
燥した後、無菌容器で保管しておく。
Example 3 Bacillus subtilis (KCTC 8662) on cotton
P) adsorption method. In order to produce a practical product by utilizing the deodorizing effect of the above-mentioned bacteria, cotton was used as a microbial cell adsorption substance. Mold cotton into a cylinder with a diameter of 1 cm and a length of 3 cm.
Sterilize at 15 ℃ for 15 minutes to remove bacteria on the raw cotton. Cylinder-shaped cotton from which germs have been removed is dried at 50 ° C in an aseptic state and then stored in a sterile container.

【0037】上記の実施例2から製造されたバチルス・
スブチルス菌(KCTC 8662P)の液状体に円筒形の
綿を漬けて、菌体が綿の内部まで十分に浸透するよう
に、1時間ぐらい漬けて置く。その後菌体が浸透した円
筒形綿を30℃の無菌乾燥機内で乾燥させた後、開口プラ
スチック容器に入れ、悪臭のひどい場所に置いた。その
後、悪臭が顕著に下がることが認められた。
Bacillus produced from Example 2 above
Cylindrical cotton is soaked in a liquid substance of subtilis bacteria (KCTC 8662P), and soaked for about 1 hour so that the bacteria can fully penetrate into the inside of the cotton. Then, the cylindrical cotton infiltrated with the bacterial cells was dried in an aseptic dryer at 30 ° C., put in an open plastic container, and placed in a place with a bad odor. After that, it was recognized that the bad odor significantly decreased.

【0038】前述したように本発明の微生物バチルス・
スブチルス菌(KCTC 8662P)は、水性栄養の添加
培地であれば、如何なる培地でも発育が良好である。培
養温度の範囲は25〜40℃であるが、最適発育温度は、30
〜35℃である。また培養 pH値の範囲は、6.5 〜8.5 の
範囲内であり、最適発育 pHは、7.0 前後としたとき
に、10〜24時間培養すれば、よく増殖することが判明し
た。
As described above, the microbial Bacillus of the present invention
Subtilis (KCTC 8662P) grows well in any medium as long as it is an aqueous nutrient supplemented medium. The range of culture temperature is 25-40 ℃, but the optimum growth temperature is 30
~ 35 ° C. Further, the range of the culture pH value was within the range of 6.5 to 8.5, and it was found that when the optimum growth pH was around 7.0, it was proliferated well by culturing for 10 to 24 hours.

【0039】[0039]

【発明の効果】上記バチルス・スブチルス菌(KCTC
8662P)は、様々な形態によく適応しながら、水,空
気及び土壌の浄化に卓越した機能を発揮する。例えば、
下水処理においては、汚水のカスを分解して悪臭を除去
し、下水管に付着した油脂成分を分解する。このような
作用は、浄化槽でも同じ効果が得られる。
EFFECTS OF THE INVENTION Bacillus subtilis (KCTC)
8662P) is well suited for a variety of forms, while exerting an outstanding function in cleaning water, air and soil. For example,
In the sewage treatment, sewage residue is decomposed to remove offensive odors, and oil and fat components attached to the sewer pipe are decomposed. With such an action, the same effect can be obtained in the septic tank.

【0040】また、淡水池,養魚池,貯水槽,冷却塔用
貯水槽及びエアコン用貯水槽に対し、上記の菌を添加す
れば、微細藻類と雑菌の発生を抑えて、水質を保全す
る。また、鶏舎,畜舎等悪臭が多発する場所に上記の菌
の液状製剤分散液を直接撒布すると、悪臭発生を抑える
ことができ、ゴミ焼却場,冷蔵庫,脱衣室,自動車,船
舶等臭いが発生する所に上記の菌を撒布し、または、容
器に入れて開放状態に置くだけでも脱臭することができ
る。
If the above-mentioned bacteria are added to the fresh water pond, the fish farm, the water storage tank, the cooling tower water storage tank, and the air conditioner water storage tank, the generation of microalgae and miscellaneous bacteria is suppressed and the water quality is maintained. In addition, if the liquid formulation dispersion liquid of the above bacteria is directly sprayed on a place where bad odors frequently occur, such as a chicken house or a livestock house, the bad odor can be suppressed, and odors such as garbage incinerators, refrigerators, dressing rooms, cars, and ships will be generated. It is possible to deodorize by sprinkling the above-mentioned bacteria on the place or by putting it in a container and leaving it open.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明によるバチルス・スブチルス(Bacillus
subtilis )菌(KCTC 8662P)の顕微鏡写真(X1
000 )である。
FIG. 1 Bacillus subtilis according to the present invention.
Subtilis) (KCTC 8662P) micrograph (X1
000).

【図2】本発明によるバチルス・スブチルス菌(KCT
C 8662P)の温度別発育度を表わすグラフである。
FIG. 2 is a Bacillus subtilis bacterium (KCT) according to the present invention.
It is a graph showing the growth degree according to temperature of C8662P).

【図3】本発明によるバチルス・スブチルス菌(KCT
C 8662P)の各 pH値による発育度を表わすグラフで
ある。
FIG. 3 is a Bacillus subtilis bacterium (KCT) according to the present invention.
It is a graph showing the growth degree by each pH value of C8662P).

【図4】本発明によるバチルス・スブチルス菌(KCT
C 8662P)の有機物分解能を表わすグラフである。
FIG. 4 is a Bacillus subtilis bacterium (KCT) according to the present invention.
It is a graph showing the organic substance resolution of C 8662P).

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 好気性の条件下で利用可能であって、炭
素源と窒素源を含む水性栄養培地での発育が良好である
ことに特徴づけられるバチルス・スブチルス菌(KCT
C 8662P)から成る下水処理用の脱臭能力を有する新
規の微生物。
1. A Bacillus subtilis bacterium (KCT) which is available under aerobic conditions and is characterized by good growth in an aqueous nutrient medium containing a carbon source and a nitrogen source.
C 8662P), a novel microorganism having deodorizing ability for sewage treatment.
【請求項2】 上記の菌の発育温度が、5〜55℃であ
り、発育 pHが、5.5〜8.5 であることを特徴とする下
水処理用の脱臭能力を有する請求項1記載の新規の微生
物。
2. The novel microorganism according to claim 1, which has a deodorizing ability for treating sewage, characterized in that the growth temperature of the bacterium is 5 to 55 ° C. and the growth pH is 5.5 to 8.5. .
【請求項3】 蒸留水1リットルに対して、澱粉8〜15
g ,ビフイクストラクト0.5 〜4g ,ペプトン7〜14g
及び塩化ナトリウム2〜7g で組成されていることを特
徴とするバチルス・スブチルス菌(KCTC 8662P)
用の培地組成物。
3. Starch 8-15 per liter of distilled water
g, bifix tract 0.5-4g, peptone 7-14g
And Bacillus subtilis (KCTC 8662P) characterized by being composed of 2 to 7 g of sodium chloride
Medium composition for use.
【請求項4】 バチルス・スブチルス菌(KCTC 86
62P)を、蒸留水1リットルに対して、澱粉8〜15g ,
ビフイクストラクト0.5 〜4g ,ペプトン7〜14g 及び
塩化ナトリウム2〜7g で組成した培地に接種した後、
25〜35℃の温度範囲及び6.5 〜8.5pHで培養することを
特徴とする微生物の培養方法。
4. Bacillus subtilis (KCTC 86)
62P) to 1 liter of distilled water, 8 to 15 g of starch,
After inoculating a medium composed of 0.5 to 4 g of bifix tract, 7 to 14 g of peptone and 2 to 7 g of sodium chloride,
A method for culturing a microorganism, which comprises culturing at a temperature range of 25 to 35 ° C. and 6.5 to 8.5 pH.
【請求項5】 バチルス・スブチルス菌(KCTC 86
62P)を、蒸留水1リットルに対して、澱粉8〜15g ,
ビフイクストラクト0.5 〜4g ,ペプトン7〜14g 及び
塩化ナトリウム2〜7g で組成した培地に接種した後、
25〜35℃の温度範囲及び6.5 〜8.5pHで培養する際に、
ポンプ式供給方式、または、固形酸素投入手段により酸
素を導入することを特徴とする微生物の培養方法。
5. Bacillus subtilis (KCTC 86)
62P) to 1 liter of distilled water, 8 to 15 g of starch,
After inoculating a medium composed of 0.5 to 4 g of bifix tract, 7 to 14 g of peptone and 2 to 7 g of sodium chloride,
When culturing in the temperature range of 25-35 ° C and 6.5-8.5 pH,
A method for culturing a microorganism, which comprises introducing oxygen by a pump-type supply system or solid oxygen introduction means.
JP8115066A 1995-05-09 1996-05-09 Noble microorganism capable of deodorization in sewage treatment, its culture medium composition and cultivation Withdrawn JPH09103290A (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
KR1019950011328A KR960041355A (en) 1995-05-09 1995-05-09 Novel microorganisms having sewage treatment and deodorizing ability, media composition and culture method thereof
KR1995/11328 1995-05-09

Publications (1)

Publication Number Publication Date
JPH09103290A true JPH09103290A (en) 1997-04-22

Family

ID=19414002

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Country Link
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KR (1) KR960041355A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0857696A2 (en) * 1997-02-05 1998-08-12 Haekang Engineering & Construction Co., Ltd. A system for treating sewage-water and a method for treating sewage-water using the same
CN1308439C (en) * 2003-02-14 2007-04-04 中国科学院南京土壤研究所 Biological denitrification method for ammonium-nitrogen containing waste water and microbes thereof
JP2010162494A (en) * 2009-01-16 2010-07-29 Yamatakagumi:Kk Deodorizing and solidifying method of sludge, and water purifying solid material and reproduction lower-layer base material produced by deodorizing and solidifying method of sludge
AU2006207887B2 (en) * 2005-09-07 2012-06-14 Neatport Pty Ltd Waste water treatment process
CN107345214A (en) * 2017-06-27 2017-11-14 江苏远山生物技术有限公司 Useless blood deodorant of a kind of composite efficient microorganism cattle and sheep and preparation method thereof

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KR100789594B1 (en) * 2006-05-10 2007-12-27 다이모스(주) Antioxidant and fermentation microorganisms for reducing odor and volatile organic compounds generated from leather, leather comprising the same and method for manufacturing same
KR102107989B1 (en) * 2019-12-20 2020-05-07 한국해양바이오클러스터 주식회사 Mass production method by medium optimization of deodorized microorganisms for reducing odor in industrial or commercial air conditioners
CN112831438B (en) * 2021-01-25 2023-05-02 瑞燃(上海)环境工程技术有限公司 Bacillus subtilis for deodorizing kitchen waste and application thereof

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0857696A2 (en) * 1997-02-05 1998-08-12 Haekang Engineering & Construction Co., Ltd. A system for treating sewage-water and a method for treating sewage-water using the same
EP0857696A3 (en) * 1997-02-05 1999-01-27 Haekang Engineering & Construction Co., Ltd. A system for treating sewage-water and a method for treating sewage-water using the same
CN1308439C (en) * 2003-02-14 2007-04-04 中国科学院南京土壤研究所 Biological denitrification method for ammonium-nitrogen containing waste water and microbes thereof
AU2006207887B2 (en) * 2005-09-07 2012-06-14 Neatport Pty Ltd Waste water treatment process
JP2010162494A (en) * 2009-01-16 2010-07-29 Yamatakagumi:Kk Deodorizing and solidifying method of sludge, and water purifying solid material and reproduction lower-layer base material produced by deodorizing and solidifying method of sludge
CN107345214A (en) * 2017-06-27 2017-11-14 江苏远山生物技术有限公司 Useless blood deodorant of a kind of composite efficient microorganism cattle and sheep and preparation method thereof

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