JP2006230332A - New microorganism and method for treating organic sludge therewith - Google Patents
New microorganism and method for treating organic sludge therewith Download PDFInfo
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本発明は、有機性汚泥の分解能力を有する新規微生物、及び、その微生物を用いた下水汚泥、各種生物性汚泥あるいは有機性汚泥の処理方法に関する。 The present invention relates to a novel microorganism capable of decomposing organic sludge and a method for treating sewage sludge, various biological sludges or organic sludge using the microorganisms.
下水道の普及に伴い、国内で発生する下水汚泥の量は年々増加する傾向にある。下水や排水などは、通常、活性汚泥法によって処理されるが、その際発生する余剰汚泥の量は、年々増加し続けており、下水余剰汚泥はわが国の産業廃棄物の割合の第一位を占めている。日本下水道協会の報告によれば、平成14年度に下水処理場で発生した汚泥の量は、4.3億m3以上に上り、その有効利用率は60%となっている。一方、残りの約40%は埋め立て処分されているが、埋立て処分地の確保が年々困難になっており、その残余年数は全国平均3.9年とされている。また、余剰汚泥、動物の糞尿やその他の有機性汚泥などの廃棄物は、資源循環としてリサイクル枠の拡大はもちろんであるが、効率的な発生抑制も方策として重要であると認識されている。 With the spread of sewerage, the amount of sewage sludge generated in the country tends to increase year by year. Sewage and wastewater are usually treated by the activated sludge method, but the amount of surplus sludge generated at that time continues to increase year by year, and sewage surplus sludge is ranked first in the proportion of industrial waste in Japan. is occupying. According to the report of the Japan Sewage Works Association, the amount of sludge generated in the sewage treatment plants in fiscal 2002, up to 430 million m 3 or more, the effective utilization rate was 60%. On the other hand, the remaining 40% is disposed of in landfills, but it has become difficult to secure landfill sites every year, and the remaining years are estimated to be 3.9 years in Japan. In addition, waste such as surplus sludge, animal manure and other organic sludge is recognized as an important measure as well as expansion of the recycling frame as a resource circulation.
そして、微生物による汚泥の処理を効率的に実施するために、有益な微生物の探索が試みられており、例えば、特開2000−139449号(特許文献1)には、バシラス属細菌に属し、アルカリ性条件下で汚泥を分解する能力を有する微生物が、特開2002−125657号(特許文献2)には、有機性汚泥や生物性汚泥に含まれるタンパク質を分解するバシラス サチリスに属する微生物が、特開2003−235547号(特許文献3)には、有機性廃棄物中及び下水汚泥中の有機物を分解消滅する能力のあるシュードモナス属に属する微生物が、特開2003−245066号(特許文献4)には、排水処理等の環境浄化に役立つロドバクター属に属する微生物が、特開2004−267127号(特許文献5)には、有機性固形物の処理に有用なバシラス属に属する微生物が開示されている。しかしながら、産業的に実用化するには、必ずしも十分なものであるとは言えない。
また、バシラス(Bacillus)属の好熱性細菌を利用した、余剰汚泥の減量化技術も提案されている(非特許文献1)。しかし、この好熱性細菌を増殖及び汚泥に作用させるためには、65℃といった高い温度が必要であり、その条件を満たすために、運転費用や設備投資などの多額の経費が避けられないという問題がある。
本発明の課題は、下水余剰汚泥等の減量化及び資源化のために、効率的で且つ取扱い易い微生物を見出すこと、そしてその微生物を用いた下水汚泥等の有機性汚泥の処理法を提供することにある。 An object of the present invention is to find an efficient and easy-to-handle microorganism for reducing and recycling sewage surplus sludge and to provide a method for treating organic sludge such as sewage sludge using the microorganism. There is.
本発明のうち請求項1記載の発明は、タンパク質分解酵素を産生し、有機性汚泥の分解能力を有する、ブレビバシラス(Brevibacillus)属細菌に属するグラム陽性の新規微生物である。 The invention described in claim 1 is a novel Gram-positive microorganism belonging to the genus Brevibacillus, which produces a proteolytic enzyme and has an ability to decompose organic sludge.
そして、請求項2記載の発明は、請求項1記載の微生物の中、更に機能特性を限定した微生物に係り、下水汚泥の重量濃度が25%である浮遊性固形分を、30〜50℃、48時間の培養で10%以上減量化させ得る溶解能を有する請求項1記載の新規微生物である。 And invention of Claim 2 concerns the microorganisms which further limited the functional characteristic among the microorganisms of Claim 1, and the floating solid content whose weight concentration of a sewage sludge is 25% is 30-50 degreeC, The novel microorganism according to claim 1, which has a lytic ability capable of being reduced by 10% or more after 48 hours of culture.
また、請求項3の発明は、独立行政法人産業技術総合研究所特許生物寄託センターに、受託番号FERM P−20399として寄託された、ブレビバシラス(Brevibacillus)sp. KH3の菌株に係るものである。なお、この菌株と実質的に同じ特性を有する限り、その変異体も請求項3の発明に含まれるものである。 The invention of claim 3 relates to a strain of Brevibacillus sp. KH3 deposited at the Patent Organism Depositary of National Institute of Advanced Industrial Science and Technology under the deposit number FERM P-20399. As long as it has substantially the same characteristics as this strain, the mutant is also included in the invention of claim 3.
更に本発明の他の態様は、請求項1〜3のいずれかに記載された微生物を用いて、有機性汚泥を可溶化することを特徴とする有機性汚泥の処理方法である。 Furthermore, another aspect of the present invention is a method for treating organic sludge, characterized in that organic sludge is solubilized using the microorganism according to any one of claims 1 to 3.
本発明のブレビバシラス(Brevibacillus)sp. KH3の菌株を利用した汚泥減量化処理は、従来の活性汚泥法において発生する下水余剰汚泥を減らす上で、新たな装置を下水処理システムに組み込む必要はない。そして、本菌株は30℃から50℃という温度領域で増殖するため、培養にかかる光熱費も比較的安価にかつ容易に実践でき、下水余剰汚泥の減量化や標準活性汚泥法の改良などの産業上の利用が期待できる。 In the sludge reduction treatment using the strain of Brevibacillus sp. KH3 of the present invention, it is not necessary to incorporate a new apparatus into the sewage treatment system in order to reduce excess sewage sludge generated in the conventional activated sludge method. And since this strain grows in the temperature range of 30 ° C to 50 ° C, the utility costs for culturing can be put into practice relatively inexpensively and in industries such as reducing the amount of excess sewage sludge and improving the standard activated sludge method. The above usage can be expected.
本発明において有機性汚泥とは、下水処理場、糞尿処理場等の下水処理プロセスから排出される生汚泥及び余剰汚泥等の生物性汚泥、あるいは食品工場、化学工場等の製造プロセス又は排水処理プロセスから排出される有機性汚泥等を全て包含するものである。そして、本発明の微生物は、タンパク質分解酵素を産生し、これらの有機性汚泥を分解する能力を有するものであり、学術的にはブレビバシラス(Brevibacillus)属細菌に属するグラム陽性の微生物である。 In the present invention, organic sludge refers to biological sludge such as raw sludge and surplus sludge discharged from sewage treatment processes such as sewage treatment plants and manure treatment plants, or manufacturing processes or wastewater treatment processes such as food factories and chemical factories. All organic sludge discharged from the plant is included. The microorganism of the present invention is capable of producing a proteolytic enzyme and decomposing these organic sludges, and is scientifically a Gram-positive microorganism belonging to the genus Brevibacillus.
かかる微生物を、本発明者らは、下水余剰汚泥の減量化及び資源化を研究目的として、50℃で馴養した余剰汚泥から、汚泥を溶解する微生物をスクリーニングすることによって見出した。即ち、馴養した汚泥を試料として、滅菌汚泥を懸濁した培地に塗布し、生育した細菌のコロニーの周囲にハローが見られるものを分離した。単離した細菌はグラム陽性の桿菌で、その菌株についての生化学的・生理学的試験及び16SリボソームRNA遺伝子DNA相同性解析の結果、ブレビバシラス(Brevibacillus)属の細菌であることが判明した。なお、これらの試験は、Bergey’s Manual of Systematic Bacteriology 第2版(1989年)に記載された方法・手段に従って行った。 The present inventors have found such microorganisms by screening microorganisms that dissolve sludge from surplus sludge conditioned at 50 ° C. for the purpose of reducing and recycling sewage surplus sludge. That is, using conditioned sludge as a sample, it was applied to a medium in which sterilized sludge was suspended, and those in which halo was observed around colonies of grown bacteria were separated. The isolated bacterium was a Gram-positive gonococcus, and as a result of biochemical and physiological tests and 16S ribosomal RNA gene DNA homology analysis, it was found to be a bacterium belonging to the genus Brevibacillus. These tests were carried out according to the methods and means described in the Bergey's Manual of Systematic Bacteriology 2nd edition (1989).
これまでブレビバシラス(Brevibacillus)属の細菌が、下水汚泥を可溶化するということは報告されていない。今回、発明者らが分離・同定した細菌株は、30℃から50℃の温度で、
下水汚泥を溶解する。この菌株についての生化学的・生理学的試験では、98%の確率でブレビバシラス ブレビス(Brevibacillus brevis)と同定された。さらに、16SリボソームRNA遺伝子のDNA相同性解析では、92%の確率でブレビバシラス(Brevibacillus) sp.RG-30及びブレビバシラス アグリ(Brevibacillus agri)と判定された。これらの結果から、本菌株はブレビバシラス(Brevibacillus)属の細菌の新菌種であると判断されるので、この細菌株をブレビバシラス(Brevibacillus) sp. KH3と命名した。
So far, it has not been reported that bacteria belonging to the genus Brevibacillus solubilize sewage sludge. The bacterial strain isolated and identified by the inventors this time is at a temperature of 30 ° C to 50 ° C.
Dissolve sewage sludge. Biochemical and physiological tests on this strain identified it as Brevibacillus brevis with a 98% probability. Furthermore, in the DNA homology analysis of the 16S ribosomal RNA gene, it was determined with a probability of 92% Brevibacillus sp. RG-30 and Brevibacillus agri. From these results, this strain was judged to be a new species of bacteria belonging to the genus Brevibacillus, so this bacterial strain was named Brevibacillus sp. KH3.
そして、この菌株は、平成17年2月14日付で、独立行政法人産業技術総合研究所特許生物寄託センターに、受託番号FERM P−20399として寄託された。 This strain was deposited at the Patent Organism Depositary, National Institute of Advanced Industrial Science and Technology on February 14, 2005, under the accession number FERM P-20399.
本発明の微生物は、グラム陽性の桿菌であり、胞子を形成する。また、LB培地上で生育良好であり、好気性の細菌である。そして、例えば、LB培地(培地1000mL当たり、バクトトリプトン10g、バクト酵母エキス粉末5g、塩化ナトリウム5gを含む、pH 7.0)で、30〜50℃で、好気性条件下で培養できる。また、LB培地で30℃、18時間培養すると、直径が約3mmの円形で、クリーム色の扁平状に隆起したコロニーを形成する。コロニーの表面形状はスムーズで、不透明でバター様の粘稠性を有している。 The microorganism of the present invention is a Gram-positive rod and forms spores. Moreover, it is an aerobic bacterium with good growth on LB medium. And it can culture | cultivate on aerobic conditions at 30-50 degreeC, for example by LB culture medium (It is pH 7.0 containing 10g of bactotryptones, 5g of bacto yeast extract powder, and 5g of sodium chloride per 1000mL of culture media. Further, when cultured in LB medium at 30 ° C. for 18 hours, a round colony having a diameter of about 3 mm and a creamy flat shape is formed. The surface shape of the colony is smooth, opaque and has a butter-like consistency.
[実施例1]細菌の分離・同定
下水余剰汚泥200 gを500 ml三角フラスコに採り、それを50℃、60 rpmで1週間振とう培養し、その培養液と新たに採取した余剰汚泥を重量比1:2となるように混合し、連続的に培養した。この操作を1週間に1回繰り返した培養液(8回連続培養)を希釈し、滅菌した余剰汚泥を懸濁した、平面寒天培地に塗布して50℃で培養し、生育した細菌のコロニーの中で、コロニーの周囲にハローの確認できるものを分離した。分離した細菌株について、生化学的・生理学的性状テスト(API20E)と炭水化物発酵テスト(API50CHB)を行い、菌株の形態学的及び生化学的・生理学的性質を調べた。その結果を表1と表2に示した。
[Example 1] Separation and identification of bacteria 200 g of excess sewage sludge was placed in a 500 ml Erlenmeyer flask and cultured with shaking at 50 ° C and 60 rpm for 1 week, and the culture and the newly collected excess sludge were weighed. The mixture was mixed at a ratio of 1: 2 and continuously cultured. Dilute the culture solution (8 times continuous culture) repeated once a week, suspend sterilized surplus sludge, apply to a flat agar medium and culture at 50 ° C. Among them, those that could be confirmed as halo were isolated around the colony. The isolated bacterial strains were subjected to biochemical and physiological properties test (API20E) and carbohydrate fermentation test (API50CHB) to examine the morphological and biochemical and physiological properties of the strain. The results are shown in Tables 1 and 2.
培養の状況及び表1と表2の結果から、この菌は、30℃から50℃の温度、pH 6.0から9.0の範囲において増殖できること、また、グラム染色及び芽胞染色、生化学的・生理学的試験〔API20E及びAPI50CHB(Biomerieux, France)〕を行った結果、好気性胞子形成グラム陽性桿菌Brevibacillus brevisとの相同性(98%)が高い菌であることが判明した。 Based on the culture conditions and the results in Tables 1 and 2, the fungus can grow in the temperature range of 30 ° C to 50 ° C and pH 6.0 to 9.0. Gram and spore staining, biochemical and physiological tests As a result of performing [API20E and API50CHB (Biomerieux, France)], it was found that the bacteria had high homology (98%) with the aerobic spore-forming gram-positive bacterium Brevibacillus brevis.
次に、微生物の進化系統の研究に最も有効な分子マーカーとして利用されている、16S リボソームRNA遺伝子のDNA相同性解析を行った。本菌株の16S リボソームRNA遺伝子をPCRによって増幅させ(63f forward primer: 5’-AGGCCTAACACATGCAAGTC-3’、1387r reverse primer: 5’-GGGCGGTGTGTACAAGGC-3’、反応条件:(1)95℃を5分間、(2)95℃を1分間、(3)50℃を1分間、(4)72℃を1.5分間、(2)から(4)のサイクルを30回、(5)72℃で5分間)、そのPCR産物をTOPO XL PCR Cloning Kit(Invitrogen, USA)を用いて、プラスミドベクターに連結させた。この16S リボソームRNA遺伝子を含むプラスミドを大腸菌へ挿入し、培養したその大腸菌からプラスミドを回収した。その後、M13 forward primer、M13 reverse primer、r2L primer(5’-CATCGTTTACGGCGTGGA-3’)、又はr3L primer (5’-TTGCGCTCGTTGCGGGACT-3’)によってシーケンス反応させ、DNAシーケンサーCEQ8000(Beckman Coulter, USA)にて塩基配列決定し、汚泥可溶化菌の16S リボソームRNA遺伝子のDNA塩基配列を得た。得られた1000塩基程度の塩基配列をもとに、代表的なDNA相同性検索エンジンであるBLAST(http://www.ddbj.nig.ac.jp/)にてシーケンスマッチを行った。その結果、表3に示すように、Brevibacillus sp. RG-30及びBrevibacillus agriと相同性が最も高かった。 Next, we analyzed the DNA homology of the 16S ribosomal RNA gene, which is used as the most effective molecular marker for the study of microbial evolutionary strains. The 16S ribosomal RNA gene of this strain was amplified by PCR (63f forward primer: 5'-AGGCCTAACACATGCAAGTC-3 ', 1387r reverse primer: 5'-GGGCGGTGTGTACAAGGC-3', reaction conditions: (1) 95 ° C for 5 minutes, ( 2) 95 ° C for 1 minute, (3) 50 ° C for 1 minute, (4) 72 ° C for 1.5 minutes, 30 cycles of (2) to (4), (5) 72 ° C for 5 minutes), PCR products were ligated to plasmid vectors using TOPO XL PCR Cloning Kit (Invitrogen, USA). The plasmid containing the 16S ribosomal RNA gene was inserted into E. coli, and the plasmid was recovered from the cultured E. coli. Then, the sequence reaction was performed with M13 forward primer, M13 reverse primer, r2L primer (5'-CATCGTTTACGGCGTGGA-3 '), or r3L primer (5'-TTGCGCTCGTTGCGGGACT-3'), and DNA sequencer CEQ8000 (Beckman Coulter, USA) The base sequence was determined, and the DNA base sequence of the 16S ribosomal RNA gene of the sludge solubilizing bacterium was obtained. Based on the obtained base sequence of about 1000 bases, sequence matching was performed with BLAST (http://www.ddbj.nig.ac.jp/) which is a typical DNA homology search engine. As a result, as shown in Table 3, the homology was highest with Brevibacillus sp. RG-30 and Brevibacillus agri.
本菌株は、生化学的・生理学的試験による同定、及び16SリボソームRNA遺伝子のDNA相同性が98%以下であること、並びに、以下の実施例2に示すように、下水汚泥を溶解することから、Brevibacillus属細菌の新菌種と判断されるので、この細菌をBrevibacillus sp. KH3株と名付けた(受託番号FERM P−20399)。 This strain is identified by biochemical and physiological tests, has a DNA homology of 98% or less of 16S ribosomal RNA gene, and dissolves sewage sludge as shown in Example 2 below. Therefore, this bacterium was named Brevibacillus sp. KH3 strain (Accession No. FERM P-20399).
[実施例2]汚泥減量化率の測定
[滅菌汚泥の調整]
下水処理場より採取した余剰汚泥300 gを500 ml三角フラスコに採り、121℃で20分間蒸気滅菌し、それを滅菌した遠沈管に移して、4℃、10,000×gで遠心した。上清を捨て、残った沈殿を滅菌精製水で3回洗浄した後、その重量濃度(w/v)が25%となるように調整した。なお、通常の下水汚泥の重量濃度は、20から30%である。
[Example 2] Measurement of sludge reduction rate [adjustment of sterilized sludge]
300 g of excess sludge collected from the sewage treatment plant was taken into a 500 ml Erlenmeyer flask, steam sterilized at 121 ° C. for 20 minutes, transferred to a sterilized centrifuge tube, and centrifuged at 4 ° C. and 10,000 × g. The supernatant was discarded, and the remaining precipitate was washed three times with sterilized purified water, and then adjusted so that its weight concentration (w / v) was 25%. The weight concentration of normal sewage sludge is 20 to 30%.
[SSの測定]
汚泥中の浮遊性固形分(suspended solid; SS)は、余剰汚泥を18,000×gで10分遠心後、上清を取り除き、沈殿を105℃で2日間乾燥させて、その重量を測定した。
[SS measurement]
The suspended solid (SS) in the sludge was centrifuged at 18,000 × g for 10 minutes, and the supernatant was removed. The precipitate was dried at 105 ° C. for 2 days, and its weight was measured.
[汚泥減量化率の測定]
LB液体培地(Tryptone:10 g/L、Yeast extract:5 g/L、NaCl:5 g/L、pH 7.0)で30℃、
120rpmで16時間前培養したBrevibacillus sp. KH3株を調整滅菌汚泥に接種し(最終菌
量約106
cfu/ml)、恒温振とう培養機にて各温度とも60 rpmで培養した。経時的にこの滅菌汚泥を採取し、SS乾燥重量が汚泥中に占める割合を0時間のものを100%として減量化率の変化を調べた。
[Measurement of sludge reduction rate]
30 ° C in LB liquid medium (Tryptone: 10 g / L, Yeast extract: 5 g / L, NaCl: 5 g / L, pH 7.0)
Brevibacillus sp. KH3 strain pre-cultured at 120 rpm for 16 hours was inoculated into the adjusted sterilized sludge (final bacteria amount of about 10 6
cfu / ml), and each temperature was cultured at 60 rpm in a constant temperature shaker. The sterilized sludge was collected over time, and the change in the weight reduction rate was examined with the SS dry weight occupying the sludge as 100%.
図1に示した様に、Brevibacillus sp. KH3株は、30℃から50℃の培養温度において、汚泥を溶解した。また、20℃および60℃の培養では、調整汚泥をほとんど溶解しなかった(データは示さず)。本菌株における、最も高い汚泥減量化率31.3%は、培養温度50℃、120時間のときであった。そして、30℃から50℃の培養温度において、48時間で、少なくとも約10%から20%の溶解率を示していることが分かる。また、同時に本菌株の増殖も見られることから(データは示さず)、Brevibacillus sp. KH3株は汚泥を溶解して、その溶解産物を炭素源及び窒素源として増殖するものと考えられる。 As shown in FIG. 1, the Brevibacillus sp. KH3 strain dissolved sludge at a culture temperature of 30 ° C. to 50 ° C. In addition, the conditioned sludge was hardly dissolved in the culture at 20 ° C. and 60 ° C. (data not shown). The highest sludge reduction rate of 31.3% in this strain was at a culture temperature of 50 ° C. for 120 hours. It can be seen that at a culture temperature of 30 ° C. to 50 ° C., a dissolution rate of at least about 10% to 20% is exhibited in 48 hours. At the same time, growth of this strain is also observed (data not shown), so it is considered that Brevibacillus sp. KH3 strain dissolves sludge and grows using the lysate as a carbon source and nitrogen source.
[実施例3]Brevibacillus sp. KH3の産出するタンパク質分解酵素
Brevibacillus sp. KH3株を、汚泥を懸濁した平面寒天培地に塗布して培養すると、形成したコロニーの周囲に汚泥を溶解したハローができる。即ち、本菌株は菌体外に、汚泥に対する可溶化因子を放出することで汚泥を溶解していると考えられる。また、本菌株をカゼインまたはスキムミルク寒天培地に塗布した場合、コロニーの周辺にハローが出来ることから、この可溶化因子はタンパク質分解酵素であることが示唆される。
[Example 3] Proteolytic enzyme produced by Brevibacillus sp. KH3
When the Brevibacillus sp. KH3 strain is applied to a flat agar medium in which sludge is suspended and cultured, a halo in which sludge is dissolved is formed around the formed colonies. That is, this strain is considered to dissolve sludge by releasing a solubilizing factor for sludge outside the cells. Moreover, when this strain is applied to casein or skim milk agar medium, a halo is formed around the colony, suggesting that this solubilizing factor is a proteolytic enzyme.
そこで、KH3株が産生するタンパク質分解酵素の活性を検討したところ、図2に示した様に、50℃で48時間培養した時に、最も高いタンパク質分解酵素活性を示すことが判明した。この48時間培養した上清をポリアクリルアミド電気泳動で調べた結果、一本の濃いバンド(分子量:約60キロダルトン)が視られた。更に、カゼインザイモグラフィー(Archives of Biochemistry and Biophysics,319,211-216(1995年)参照 )によって、タンパク質分解酵素の活性を確認することができた。以上の結果から、汚泥可溶化因子はタンパク質分解酵素であることが判明した。 Then, when the activity of the proteolytic enzyme produced by the KH3 strain was examined, it was found that the highest proteolytic enzyme activity was exhibited when cultured at 50 ° C. for 48 hours as shown in FIG. As a result of examining the supernatant cultured for 48 hours by polyacrylamide electrophoresis, one thick band (molecular weight: about 60 kilodaltons) was observed. Furthermore, the activity of proteolytic enzyme could be confirmed by casein zymography (see Archives of Biochemistry and Biophysics, 319, 211-216 (1995)). From the above results, it was found that the sludge solubilizing factor is a proteolytic enzyme.
本発明は、下水処理場や工場の排水処理施設など、有機性汚泥を活性汚泥法等を用いて処理を行っている施設において、用いる微生物や処理方法の改善・改良等に利用することができる。 INDUSTRIAL APPLICABILITY The present invention can be used for improvement or improvement of microorganisms to be used or a treatment method in a facility that treats organic sludge using an activated sludge method or the like, such as a sewage treatment plant or a factory wastewater treatment facility .
Claims (4)
A method for treating organic sludge, comprising solubilizing organic sludge using the novel microorganism according to any one of claims 1 to 3.
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CN116332324A (en) * | 2023-02-23 | 2023-06-27 | 杭州洛奇亚环保科技有限公司 | Electrochemical enhanced aerobic microorganism diaphragm-free wastewater electrolysis device |
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