JP2010227858A - Method of treating fat-containing wastewater by lipase secretion microorganisms capable of propagation/fat splitting under weak acid conditions, grease trap cleaning method and fat-splitting agent - Google Patents

Method of treating fat-containing wastewater by lipase secretion microorganisms capable of propagation/fat splitting under weak acid conditions, grease trap cleaning method and fat-splitting agent Download PDF

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JP2010227858A
JP2010227858A JP2009079432A JP2009079432A JP2010227858A JP 2010227858 A JP2010227858 A JP 2010227858A JP 2009079432 A JP2009079432 A JP 2009079432A JP 2009079432 A JP2009079432 A JP 2009079432A JP 2010227858 A JP2010227858 A JP 2010227858A
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grease trap
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Katsutoshi Hori
克敏 堀
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Nagoya Institute of Technology NUC
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Abstract

<P>PROBLEM TO BE SOLVED: To effectively treat wastewater containing high-concentration fat and oil like kitchen wastewater by highly efficiently degrading fat and oil by microorganisms. <P>SOLUTION: The fat and oil are degraded by lipase secretion microorganisms capable of propagation/fat-splitting under the same weak acid conditions as the inside of a grease trap. By using the method of treating the fat-containing wastewater, oil accumulated in the grease trap is removed inside a trap tank. <P>COPYRIGHT: (C)2011,JPO&INPIT

Description

本発明は弱酸性条件で増殖・油脂分解可能なリパーゼ分泌微生物による油脂含有排水の処理方法とグリーストラップ浄化方法及び油脂分解剤に関するものである。   The present invention relates to a method for treating fat-containing wastewater by a lipase-secreting microorganism capable of growing and decomposing oil under mildly acidic conditions, a method for purifying grease traps, and an oil-degrading agent.

外食産業の厨房排水に含まれる油分を固液分離により除く処理設備であるグリーストラップでは、悪臭や害虫の発生源であること、分離した油の回収や運搬、清掃等のメンテナンスにかかる労苦やコストなどを考慮すると、グリーストラップ内の油を消滅させるような画期的な技術の確立が、外食産業を中心とする産業界から切望されている。そこで、微生物による油脂分解技術の適用が試みられてきた。そのような試みの多くは、油脂分解能力の優れた微生物を単離し、油脂分解能力を調べたり実際にグリーストラップに適用してみたりというものである(例えば特許文献1から6)。実際、油脂分解菌を含むグリーストラップ用微生物製剤が多数、市販されている。
しかしながら、外食産業の厨房排水は通常1g/L以上、高いときは10g/L以上もの高濃度の油脂を含んでいるだけでなく、多くのグリーストラップ内の排水の滞留時間は10分程度と極めて短い。そのため、グリーストラップ内だけで油を処理することは困難であり、これまでのところ、多くの自治体が設定している排出目標であるノルマルヘキサン値30mg/Lを、グリーストラップ内の処理だけで常時達成できる油脂分解微生物は報告されていない。
実際に先に例示した特許文献3から5は、フラスコまたは水槽を用いた実証例しか示していない。また、特許文献2および6では、グリーストラップの外に油脂分解槽を設けており、その中で分解処理している。さらにこれらの実施例においては、30から300mg/Lという、通常の排水よりずっと低濃度の油脂を分解した実施例しか示されていない。特許文献1では、グリーストラップ内で処理した実施例が示されているが、連続運転の結果が示されておらず、また、前述の排出目標値よりも一桁高い値までしか処理されていない結果が示されている。したがって、グリーストラップ内だけで油を処理するには、微生物による分解効率をさらに向上させる必要がある。
また、市販微生物製剤の多くは、実験室レベルの培養では油脂分解に効果的であるが、グリーストラップ槽内に投入しても期待した油脂分解効果を示さない。よって、実際のグリーストラップ内においても高い増殖能力と油脂分解能力を示す微生物を開発する必要がある。
Grease traps, which are processing equipment that removes oil contained in kitchen wastewater from the food service industry by solid-liquid separation, are sources of malodors and pests, and labor and costs associated with maintenance, such as recovery, transportation, and cleaning of the separated oil In view of the above, the establishment of a revolutionary technology that eliminates the oil in the grease trap is eagerly desired by the industry, particularly the restaurant industry. Accordingly, attempts have been made to apply a technique for decomposing oils and fats using microorganisms. Many of such attempts are to isolate microorganisms having an excellent ability to decompose fats and oils, to examine the ability to decompose fats and oils, and to actually apply them to grease traps (for example, Patent Documents 1 to 6). In fact, many microbial preparations for grease traps containing oil-degrading bacteria are commercially available.
However, kitchen wastewater in the food service industry usually contains high concentrations of fats and oils of 1 g / L or more, and when high, 10 g / L or more, and the residence time of the wastewater in many grease traps is about 10 minutes. short. For this reason, it is difficult to treat oil only in the grease trap, and so far, the normal hexane value of 30 mg / L, which is an emission target set by many local governments, is always achieved only by treatment in the grease trap. No fat-degrading microorganisms that can be achieved have been reported.
Patent Documents 3 to 5 actually exemplified above show only demonstration examples using a flask or a water tank. Moreover, in patent document 2 and 6, the fats-and-oils decomposition tank is provided in addition to the grease trap, and it decomposes | disassembles in it. Further, in these examples, only examples in which fats and oils having a concentration of 30 to 300 mg / L, which is much lower than normal waste water, are decomposed are shown. In Patent Document 1, an example of processing in a grease trap is shown, but the result of continuous operation is not shown, and processing is performed only up to an order of magnitude higher than the aforementioned discharge target value. Results are shown. Therefore, in order to process the oil only in the grease trap, it is necessary to further improve the decomposition efficiency by microorganisms.
In addition, many commercially available microbial preparations are effective in decomposing fats and oils in laboratory culture, but do not show the expected decomposing effects even when put in a grease trap tank. Therefore, it is necessary to develop a microorganism exhibiting a high growth ability and fat / oil decomposition ability even in an actual grease trap.

特開平11−75832号公報JP-A-11-75832 特開2003−24051号公報Japanese Patent Laid-Open No. 2003-24051 特開2003−38169号公報JP 2003-38169 A 特開2004−242553号公報JP 2004-242553 A 特開2008−142042号公報JP 2008-144202 A 特開2008−220201号公報JP 2008-220201 A

本発明は、上記した事情に鑑みてなされたもので、弱酸性条件で増殖・油脂分解可能なリパーゼ分泌微生物によって油脂含有排水を効果的に処理するための方法と油脂分解剤を提供することを第一の目的とし、それよって厨房排水のような高濃度油脂含有排水を効果的に処理することを第二の目的とする。 The present invention has been made in view of the above circumstances, and provides a method and an oil decomposing agent for effectively treating oil-containing wastewater by a lipase-secreting microorganism capable of growing and degrading oil under mildly acidic conditions. The first object is to treat the wastewater containing high concentration fats and oils such as kitchen wastewater effectively.

油脂含有排水は、内在する微生物等の働きにより油脂の一部が加水分解され、pH5.5からpH6.0ぐらいの弱酸性となっている場合が多い。そこで本発明者は、弱酸性条件でも増殖・油脂分解可能なリパーゼ分泌微生物ならば、実際の油脂含有排水中の油を効果的に除去し、グリーストラップの浄化効果も高いと考えた。
そのために、本発明は、弱酸性の条件でも油脂を分解して増殖可能なリパーゼ分泌微生物により油脂を分解する油脂含有排水処理方法を特徴とする(請求項1)。さらに、請求項1に記載の油脂含有排水処理方法において、リパーゼ分泌微生物がバークホルデリア アルボリス(Burkholderia arbolis)であることを特徴とする(請求項2)。また、請求項1または2に記載の油脂含有排水の処理方法により、グリーストラップに蓄積した油分をトラップ槽内で除去し、グリーストラップを浄化する方法を特徴とする(請求項3)。
また、弱酸性の条件でも油脂を分解して増殖可能なリパーゼ分泌微生物を含む油脂分解剤を特徴とする(請求項4)。さらに、請求項4に記載の油脂分解剤において、リパーゼ分泌微生物がバークホルデリア アルボリスであることを特徴とする(請求項5)。
本発明による上記の方法と油脂除去剤を利用すれば、高濃度の油脂を含む厨房排水を処理する施設であるグリーストラップ内で油を分解処理して浄化することも可能である。
In many cases, fats and oils-containing wastewater is weakly acidic at a pH of about 5.5 to about 6.0 because a part of the oils and fats is hydrolyzed by the action of microorganisms and the like. Therefore, the present inventor considered that a lipase-secreting microorganism capable of growing and decomposing even under weakly acidic conditions effectively removes oil in the actual oil-containing wastewater and has a high purification effect of the grease trap.
To this end, the present invention is characterized by a method for treating fat and oil containing wastewater by decomposing oil and fat with a lipase-secreting microorganism capable of decomposing and growing oil and fat even under mildly acidic conditions (claim 1). Furthermore, in the method for treating fat and oil-containing wastewater according to claim 1, the lipase-secreting microorganism is Burkholderia arbolis (claim 2). Further, the method for treating oil-containing wastewater according to claim 1 or 2 is characterized in that the oil accumulated in the grease trap is removed in the trap tank to purify the grease trap (claim 3).
Further, the present invention is characterized by an oil and fat decomposing agent containing a lipase-secreting microorganism capable of decomposing and growing oil and fat even under weakly acidic conditions. Furthermore, in the oil and fat decomposing agent according to claim 4, the lipase-secreting microorganism is Burkholderia alboris (claim 5).
If the above-described method and fat removing agent according to the present invention are used, it is also possible to decompose and purify the oil in a grease trap, which is a facility for treating kitchen wastewater containing a high concentration of fat.

比較例1における市販の微生物製剤を、pH7(丸印)またはpH6(四角印)の油脂含有培地にて培養した時の培地濁度の変化を示すグラフである。It is a graph which shows the change of the medium turbidity when the commercially available microorganism preparation in the comparative example 1 is cultured in the fat and oil containing medium of pH7 (circle mark) or pH6 (square mark). 実施例1におけるバークホルデリア アルボリスSL1B1株を、pH7(丸印)またはpH6(四角印)の油脂含有培地にて培養した時の培地の濁度の変化を示すグラフである。It is a graph which shows the change of the turbidity of a culture medium when the Burkholderia arboris SL1B1 strain in Example 1 is cultured in a fat and oil containing medium of pH 7 (circle mark) or pH 6 (square mark). 実施例2におけるバークホルデリア アルボリスSL1B1株のCFU、リパーゼ活性、全脂肪酸濃度、アンモニウムイオン濃度の経時的変化を示すグラフである。It is a graph which shows the time-dependent change of CFU, lipase activity, total fatty acid concentration, and ammonium ion concentration of Burkholderia arboris SL1B1 strain in Example 2.

次に、本発明の実施形態について説明するが、本発明の技術的範囲は、これらの実施形態によって限定されるものではなく、発明の要旨を変更することなく様々な形態で実施することができる。また、本発明の技術的範囲は、均等の範囲にまで及ぶものである。
本発明で用いる微生物は、弱酸性の条件でも増殖・油脂分解可能なリパーゼ分泌微生物である。そのような微生物は、油脂を唯一の炭素源として含みかつpHを6に調整した無機塩寒天培地上で単離可能である。また、リパーゼ分泌微生物は、上記寒天培地上に生じたコロニー周辺にクリアゾーン(ハロー)を形成するので判別可能である。実際にこれらの方法により、弱酸性の条件下でもリパーゼを分泌して油脂を分解し増殖する能力が高い微生物としてSL1B1株を単離した。16SリボゾームDNAの塩基配列の決定及び系統解析によって、この微生物はバークホルデリア アルボリスと同定され、平成21年3月17日に独立行政法人製品評価技術基盤機構特許微生物寄託センターに受領された。受領番号はNITE AP-724である。
弱酸性の条件でもリパーゼを分泌して油脂を分解し増殖する微生物としては、真性細菌、酵母、糸状真菌類が例示される。これらのうち好ましくは真性細菌と酵母、さらに好ましくはグラム陽性細菌、プロテオバクテリアがよい。またグラム陽性細菌の中ではバチルス属細菌が特によい。プロテオバクテリアの中ではアルファバクテリア、ベータバクテリア、ガンマバクテリアがさらに好ましい。さらにこの中でも、バークホルデリア属細菌、アシネトバクター(Acinetobacter)属細菌、シュードモナス(Pseudomonas)属細菌、アルカリゲネス(Alcaligenes)属細菌、ロドバクター(Rhodobacter)属細菌、ラルストニア(Ralstonia)属細菌、アシドボラックス(Acidovorax)属細菌は、前述のグラム陽性細菌に属するバチルス属細菌と並んで、特に好ましい。さらにこれら真性細菌の属の中ではバークホルデリア属細菌が最も好ましい。バークホルデリア属細菌の中では、バークホルデリア アルボリスが最も好ましい。その実例として、前述のバークホルデリア アルボリスSL1B1株を挙げることができる。
微生物のリパーゼ分泌能力については、微生物培養液の遠心分離によって得られる培養上清のリパーゼ活性を測定することにより評価することができる。リパーゼ活性は、パルミチン酸と4−ニトロフェノールとのエステルである4−ニトロフェニルパルミテート(4−NPP)を基質として用いて酵素反応を行い、エステルの加水分解により生じたp−ニトロフェノールの量を410nmの吸光度を測定することによって決定できる。まず、4−NPP(18.9mg)を3%(v/v)トリトンX―100(12ml)に加え、70℃で溶解して基質溶液とする。基質溶液1mL、イオン交換水0.9mLおよび150mM GTA緩衝液(150mM 3,3−dimethylglutaric acid,150mM Tris,および150mM 2−amino−2−methyl−1,3−propanediolにNaOHまたはHClを加えてpH6に調製)1mLをセルに入れ、28℃で5分間保温する。これに培養上清を0.1mL添加して、攪拌しながら410nmの値を測定する。リパーゼ活性は、1μモルの4−ニトロフェノールを生産する酵素量を1ユニット(U)と定義して活性測定を行い、培養上清1mL当たりのユニットを算出する。
微生物の油脂と脂肪酸の分解・消費能力は、培地中に残存する油脂に含まれる脂肪酸および加水分解により生じた遊離脂肪酸をガスクロマトグラフィーで定量することにより評価できる。具体的な定量手順を示すと、まず、培養上清1mLを塩酸により酸性にし、2mLのクロロホルムを加える。2分間攪拌後遠心し、クロロホルム層1mLを別容器に移して溶媒を蒸発させて濃縮する。メタノリシス溶液(メタノール:硫酸=17:3)を2mL加えて100℃で2時間加熱し、油脂および遊離脂肪酸をメチルエステル化させる。その後、クロロホルム2mL、純水1mLを加えて攪拌の後、クロロホルム層をガスクロマトグラフィーで分析し、脂肪酸のメチルエステルを定量する。
微生物の増殖能力を調べる方法としては、菌体の光学密度として660nmの吸光度(濁度)(OD660)を測定する方法や、コロニーフォーミングユニット(CFU)を測定する方法などがある。後者では、寒天培地上に培養液の原液および希釈液を一定量塗り拡げ、静置培養により形成されたコロニーを計数する。
微生物および油脂分解剤としては、液体の形状でも固体の形状でもよい。液体形状のものとしては、微生物の培養液そのもの、微生物を遠心分離などにより集菌したものを水などに再度分散させたものなどが例示される。固体形状のものは、例えば培養菌体を凍結乾燥することによって得ることができ、粉末、顆粒、錠剤などにできる。また、微生物を各種担体に固定化してもよい。
油脂分解剤は、例えばバークホルデリア アルボリスSL1B1株のような弱酸性条件で増殖・油脂分解可能なリパーゼ分泌微生物を少なくとも一種類含んでいれば、それ以上の種類の微生物や、微生物の活性を高めたり、長期間維持したりするための物質を含んでいても構わない。
本発明による油脂の分解技術および油脂分解剤は、グリーストラップはもちろん、油脂を含有するあらゆる排水の処理に適用可能である。また、グリーストラップに適用する際は、別に分解処理槽を設けてもよいが、油脂分解剤や微生物を直接グリーストラップに投入してグリーストラップ内で分解処理することもできる。
Next, embodiments of the present invention will be described, but the technical scope of the present invention is not limited by these embodiments, and can be implemented in various forms without changing the gist of the invention. . Further, the technical scope of the present invention extends to an equivalent range.
The microorganism used in the present invention is a lipase-secreting microorganism that can grow and decompose oils and fats even under mildly acidic conditions. Such microorganisms can be isolated on an inorganic salt agar medium containing fat and oil as the sole carbon source and adjusted to pH 6. In addition, lipase-secreting microorganisms can be identified because they form a clear zone (halo) around the colony formed on the agar medium. In fact, the SL1B1 strain was isolated by these methods as a microorganism having a high ability to secrete lipase, decompose oils and fats even under mildly acidic conditions. This microorganism was identified as Burkholderia arboris by determination of the base sequence of 16S ribosomal DNA and phylogenetic analysis, and it was received on March 17, 2009 by the National Institute for Product Evaluation Technology Patent Microorganism Depositary. The receipt number is NITE AP-724.
Examples of microorganisms that secrete lipase and decompose fats and oils under mildly acidic conditions include true bacteria, yeasts, and filamentous fungi. Of these, preferred are true bacteria and yeast, and more preferred are Gram-positive bacteria and proteobacteria. Among Gram-positive bacteria, Bacillus bacteria are particularly good. Among the proteobacteria, alpha bacteria, beta bacteria, and gamma bacteria are more preferable. Furthermore, among them, Burkholderia bacteria, Acinetobacter bacteria, Pseudomonas bacteria, Alcaligenes bacteria, Rhodobacter bacteria, Ralstonia bacteria, Acidborax The genus bacteria are particularly preferred along with the Bacillus bacteria belonging to the aforementioned gram-positive bacteria. Furthermore, among these genus of true bacteria, Burkholderia bacteria are most preferable. Of the Burkholderia bacteria, Burkholderia arboris is most preferred. As an example, the above-mentioned Burkholderia arboris SL1B1 strain can be mentioned.
The ability of the microorganism to secrete lipase can be evaluated by measuring the lipase activity of the culture supernatant obtained by centrifugation of the microorganism culture solution. The lipase activity is the amount of p-nitrophenol produced by enzymatic reaction using 4-nitrophenyl palmitate (4-NPP), which is an ester of palmitic acid and 4-nitrophenol, as a substrate. Can be determined by measuring the absorbance at 410 nm. First, 4-NPP (18.9 mg) is added to 3% (v / v) Triton X-100 (12 ml) and dissolved at 70 ° C. to obtain a substrate solution. PH 6 by adding NaOH or HCl to 1 mL of substrate solution, 0.9 mL of ion exchange water and 150 mM GTA buffer (150 mM 3,3-dimethyllactic acid, 150 mM Tris, and 150 mM 2-amino-2-methyl-1,3-propandiol) 1 mL is put into a cell and kept at 28 ° C. for 5 minutes. 0.1 mL of the culture supernatant is added thereto, and the value at 410 nm is measured while stirring. The lipase activity is measured by defining the amount of enzyme that produces 1 μmol of 4-nitrophenol as 1 unit (U), and the unit per 1 mL of culture supernatant is calculated.
The ability of the microorganisms to decompose and consume fatty acids and fatty acids can be evaluated by quantifying the fatty acids contained in the fats and oils remaining in the medium and the free fatty acids generated by hydrolysis by gas chromatography. Specifically, 1 mL of the culture supernatant is acidified with hydrochloric acid, and 2 mL of chloroform is added. After stirring for 2 minutes, the mixture is centrifuged, and 1 mL of the chloroform layer is transferred to another container, and the solvent is evaporated to concentrate. 2 mL of methanolysis solution (methanol: sulfuric acid = 17: 3) is added and heated at 100 ° C. for 2 hours to methylate the fats and oils and free fatty acids. Thereafter, 2 mL of chloroform and 1 mL of pure water are added and stirred, and then the chloroform layer is analyzed by gas chromatography to quantify the fatty acid methyl ester.
As a method for examining the growth ability of microorganisms, there are a method of measuring absorbance (turbidity) (OD660) at 660 nm as an optical density of bacterial cells, a method of measuring colony forming unit (CFU), and the like. In the latter, a certain amount of the stock solution and the diluted solution of the culture solution are spread on the agar medium, and colonies formed by stationary culture are counted.
The microorganism and the oil / fat decomposer may be in a liquid form or a solid form. Examples of the liquid form include a microorganism culture solution itself, a microorganism collected by centrifugation or the like, and dispersed again in water or the like. The solid form can be obtained, for example, by freeze-drying cultured cells, and can be made into powder, granules, tablets, and the like. Moreover, you may fix microorganisms to various support | carriers.
If the fat and oil decomposer contains at least one kind of lipase-secreting microorganism that can be grown and decomposed under mildly acidic conditions such as Burkholderia arboris SL1B1, it will increase the activity of more kinds of microorganisms and microorganisms. Or may contain a substance for maintaining for a long time.
The oil-and-fat decomposition technology and the oil-and-oil decomposer according to the present invention can be applied to the treatment of all wastewater containing oil and fat as well as grease traps. In addition, when applied to a grease trap, a separate decomposition treatment tank may be provided, but it is also possible to introduce an oil and fat decomposing agent or a microorganism directly into the grease trap and perform the decomposition treatment in the grease trap.

実施例1として、pH7またはpH6に調製した無機塩培地(20mL)に、10g/Lのキャノーラ油を添加し、これにバークホルデリア アルボリスSL1B1株を植菌し、28℃にて振とう培養した。経時的に培地を採取し、OD660を測定することで、両pHにおける菌体の増殖能力を調べた。また比較例1として、市販の微生物製剤を同条件で培養し、OD660を測定した。
OD660の測定結果を、図1(比較例1)および図2(実施例1)に記載した。比較例1の市販微生物は、pH7では増殖できるがpH6では増殖できないことがわかる。それに対し、実施例1に示したバークホルデリア アルボリスSL1B1株は、pH7ではもちろんpH6でも良好に増殖できることが明らかである。
実施例2として、5Lファーメンターを用いて、10g/Lのキャノーラ油を含む無機塩培地(3L)にリパーゼ分泌細菌バークホルデリア アルボリスSL1B1株を植菌し、28℃、pH6に制御して攪拌培養した。経時的に培地を採取し、CFU、油脂に含まれる脂肪酸と遊離の脂肪酸を合わせた全脂肪酸量、アンモニウムイオン濃度、およびリパーゼ活性を測定した。その結果を図3に示す。pH6の条件でもバークホルデリア アルボリスSL1B1株は窒素源であるアンモニウムイオン(三角印)を消費し、CFU(ダイヤモンド印)の増加に示されるとおり、盛んに増殖することが改めて示された。また、pH6でもリパーゼを分泌することがリパーゼ活性(白丸印)の測定によって明確に示され、実際に全脂肪酸量(黒丸印)は低下し、40時間以内に完全に分解された。すなわち、10g/L分の油が完全に除去された。
バークホルデリア アルボリスSL1B1株を含む油脂除去剤を実際にグリーストラップに投与する実験を実施した。グリーストラップは大学生協の設備を使用し、その構成については従来公知のものと同様なので詳しい説明は省略するが、概略を述べると、板で仕切った3槽から成り、各槽間は下部でつながっている。排水は第1槽へ流入し、下部の開放部を通じて第2槽、さらには第3槽へと流れ、最終的に第3槽から流出する。内容量は200Lであり、排水の平均滞留時間は12分である。油脂除去剤の投与は、生協食堂厨房からの排水の流入・流出が夜間に止まった直後に実施し、ノルマルヘキサン値測定のための採水は、油脂除去剤の添加前と、翌朝に排水の流入・流出が再び始まる直前に行った。400mLの油脂除去剤を毎晩、第1槽に投入した。
As Example 1, 10 g / L canola oil was added to an inorganic salt medium (20 mL) adjusted to pH 7 or pH 6, and Burkholderia arboris SL1B1 strain was inoculated thereto, and cultured with shaking at 28 ° C. . The culture medium was collected over time, and OD660 was measured to examine the ability of the cells to grow at both pHs. Moreover, as Comparative Example 1, a commercially available microbial preparation was cultured under the same conditions, and OD660 was measured.
The measurement results of OD660 are shown in FIG. 1 (Comparative Example 1) and FIG. 2 (Example 1). It can be seen that the commercially available microorganism of Comparative Example 1 can grow at pH 7, but cannot grow at pH 6. In contrast, it is clear that the Burkholderia arboris SL1B1 strain shown in Example 1 can grow well at pH 7 as well as at pH 7.
As Example 2, a 5 L fermenter was used to inoculate the lipase-secreting bacterium Burkholderia arboris SL1B1 strain in an inorganic salt medium (3 L) containing 10 g / L of canola oil, and the mixture was stirred at 28 ° C. and pH 6 and stirred. Cultured. The medium was collected over time, and the total fatty acid amount, the ammonium ion concentration, and the lipase activity were determined by combining CFU, the fatty acid contained in the oil and fat, and the free fatty acid. The result is shown in FIG. It was again shown that the Burkholderia arboris SL1B1 strain consumed ammonium ions (triangles) as a nitrogen source and proliferated vigorously as indicated by an increase in CFU (diamonds) even under pH 6 conditions. Moreover, it was clearly shown by the measurement of lipase activity (open circles) that the lipase was secreted even at pH 6, and the total amount of fatty acids (filled circles) actually decreased and was completely decomposed within 40 hours. That is, 10 g / L of oil was completely removed.
An experiment was conducted in which an oil removing agent containing Burkholderia arboris SL1B1 strain was actually administered to the grease trap. The grease trap uses the facilities of the university co-op, and its configuration is the same as that conventionally known, so a detailed explanation is omitted. However, the outline is composed of three tanks partitioned by plates, and each tank is connected at the bottom. ing. The drainage flows into the first tank, flows through the lower opening to the second tank and further to the third tank, and finally flows out from the third tank. The internal volume is 200 L, and the average residence time of the waste water is 12 minutes. The fat removal agent should be administered immediately after the inflow and outflow of wastewater from the Co-op cafeteria kitchen stopped at night, and water for measurement of normal hexane values should be collected before the addition of the fat removal agent and the next morning. We went just before the inflow and outflow began again. 400 mL of the oil and fat removing agent was put into the first tank every night.

油脂除去剤を添加してグリーストラップ内で油の分解処理をした結果を表1に示す。油脂除去剤を使用していないとき、油脂除去剤の投与を開始した初日、連続投与一週間後、三週間後のノルマルヘキサン値(mg/L)を、それぞれ比較例2、実施例3、実施例4、実施例5として示す。表1に記した結果から明らかにように、本発明品である油脂除去剤は、グリーストラップ内においても顕著な油分の低減効果がありグリーストラップの浄化に有効であることがわかった。

Table 1 shows the results of adding oil removing agent and decomposing oil in the grease trap. When the oil removing agent was not used, the first day when the administration of the oil removing agent was started, the normal hexane value (mg / L) after one week and three weeks after the continuous administration were respectively shown in Comparative Example 2, Example 3, and Examples 4 and 5 are shown. As is apparent from the results shown in Table 1, it was found that the oil and fat removing agent according to the present invention has a significant oil content reducing effect even in the grease trap and is effective for purification of the grease trap.

Claims (5)

弱酸性の条件でも油脂を分解して増殖可能なリパーゼ分泌微生物により油脂を分解することを特徴とする油脂含有排水処理方法。 A fat and oil-containing wastewater treatment method comprising decomposing oil and fat with a lipase-secreting microorganism capable of decomposing and growing under mildly acidic conditions. 前記リパーゼ分泌微生物がバークホルデリア アルボリス(Burkholderia arbolis)である請求項1に記載の油脂含有排水処理方法。 The fat-and-oil wastewater treatment method according to claim 1, wherein the lipase-secreting microorganism is Burkholderia arbolis. 請求項1または2に記載の油脂含有排水の処理方法により、グリーストラップに蓄積した油分をトラップ槽内で除去することを特徴とするグリーストラップ浄化方法。 A method for purifying a grease trap, wherein oil accumulated in a grease trap is removed in a trap tank by the method for treating oil-containing wastewater according to claim 1 or 2. 弱酸性の条件でも油脂を分解して増殖可能なリパーゼ分泌微生物を含む油脂分解剤。 An oil and fat degrading agent containing lipase-secreting microorganisms that can decompose and grow even under mildly acidic conditions. 前記リパーゼ分泌微生物がバークホルデリア アルボリスである請求項4に記載の油脂分解剤。 The fat and oil decomposing agent according to claim 4, wherein the lipase-secreting microorganism is Burkholderia arboris.
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