JP2002143830A - Method for decomposing and removing pollutant by microorganism and additive for decomposition of pollutant to be used for the method - Google Patents

Method for decomposing and removing pollutant by microorganism and additive for decomposition of pollutant to be used for the method

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Publication number
JP2002143830A
JP2002143830A JP2000347529A JP2000347529A JP2002143830A JP 2002143830 A JP2002143830 A JP 2002143830A JP 2000347529 A JP2000347529 A JP 2000347529A JP 2000347529 A JP2000347529 A JP 2000347529A JP 2002143830 A JP2002143830 A JP 2002143830A
Authority
JP
Japan
Prior art keywords
compost
polycyclic aromatic
decomposing
contaminant
aromatic hydrocarbons
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.)
Pending
Application number
JP2000347529A
Other languages
Japanese (ja)
Inventor
Yoji Ishikawa
洋二 石川
Hiroyuki Chino
裕之 千野
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.)
Obayashi Corp
Original Assignee
Obayashi Corp
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 Obayashi Corp filed Critical Obayashi Corp
Priority to JP2000347529A priority Critical patent/JP2002143830A/en
Publication of JP2002143830A publication Critical patent/JP2002143830A/en
Pending legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/78Recycling of wood or furniture waste

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  • Processing Of Solid Wastes (AREA)
  • Fire-Extinguishing Compositions (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)

Abstract

PROBLEM TO BE SOLVED: To rapidly decompose hardly decomposable polycyclic aromatic hydrocarbons such as tetracyclic pyrene and pentacyclic benzopyrene. SOLUTION: In the method for decomposing and removing pollutants by microorganisms, compost of sheep feces is first used as a compost and subjected to secondary fermentation with wooden material. As for the wooden material, for example, sawdust can be used. Then the secondary fermented substance obtained by fermenting the compost of sheet feces with sawdust as the wooden material is added and mixed to the oil-polluted soil as a polluted material containing polycyclic aromatic hydrocarbons(PAH) such as phenanthrene, anthracene, fluoranthene, pyrene, chrysene or the like as the pollutants.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は、微生物による汚染
物質の分解除去方法及びそれに用いる汚染物質分解用添
加剤に関する。
TECHNICAL FIELD The present invention relates to a method for decomposing and removing contaminants by microorganisms and an additive for decomposing contaminants used therein.

【0002】[0002]

【従来の技術】最近、微生物によって汚染物質を分解し
無害化する、いわゆるバイオレメディエーションなる手
法が注目されている。
2. Description of the Related Art Recently, a technique called bioremediation, in which contaminants are decomposed and rendered harmless by microorganisms, has attracted attention.

【0003】バイオレメディエーションとは、細菌やか
びなどの微生物の分解能力を利用して汚染物質を分解
し、無害化する方法であり、汚染物質が含まれた土壌な
どを微生物の活動に最適な水分・栄養・通気などの環境
に調整して微生物の活性を向上させることにより、自然
状態よりも効率よく汚染物質の分解を行うことができ
る。
[0003] Bioremediation is a method of decomposing and detoxifying contaminants by utilizing the decomposing ability of microorganisms such as bacteria and fungi. -By improving the activity of microorganisms by adjusting the environment such as nutrition and ventilation, it is possible to decompose pollutants more efficiently than in the natural state.

【0004】かかるバイオレメディエーションは、物理
処理や化学処理のように薬剤を一切使用しないので、低
コストであるとともに安全性も高く、今後ますます適用
範囲が拡がっていくものと期待されている。
[0004] Such bioremediation does not use any chemical agent such as physical treatment or chemical treatment, so it is low in cost and high in safety, and it is expected that its application will be further expanded in the future.

【0005】[0005]

【発明が解決しようとする課題】ここで、例えば原油で
汚染された土壌をバイオレメディエーションで浄化しよ
うとする場合、原油の主成分である炭素原子数5〜40程
度の各種炭化水素化合物は、分子構造のタイプによっ
て、パラフィン系、オレフィン系などのいわゆる脂肪族
炭化水素と、芳香族炭化水素に概ね大別され、これらの
うち、脂肪族炭化水素や比較的簡単な構造の芳香族炭化
水素、例えば2環を含むアセナフテン、フルオレン、3
環を含むフェナントレン、フルオランテンなどについて
は、土中に含まれている細菌類で比較的容易に分解する
ことが可能であり、その意味でこれらの物質は、易分解
性の炭化水素として分類できる。
Here, for example, in a case where soil contaminated with crude oil is to be purified by bioremediation, various hydrocarbon compounds having about 5 to 40 carbon atoms, which are the main components of crude oil, have a molecular Depending on the type of structure, paraffins, so-called aliphatic hydrocarbons such as olefins, and aromatic hydrocarbons are roughly classified, and among these, aliphatic hydrocarbons and aromatic hydrocarbons having a relatively simple structure, for example, Acenaphthene, fluorene, and 3 containing two rings
Ring-containing phenanthrene, fluoranthene and the like can be relatively easily decomposed by bacteria contained in the soil, and in that sense, these substances can be classified as easily degradable hydrocarbons.

【0006】これに対し、4環のピレン、5環のベンゾ
ピレンといった複雑な構造の多環芳香族炭化水素は、難
分解性炭化水素と言われており、通常の土中菌では1年
の期間を費やしても十分に分解することができないとい
う問題を生じていた。
On the other hand, polycyclic aromatic hydrocarbons having a complicated structure, such as 4-ring pyrene and 5-ring benzopyrene, are said to be hardly degradable hydrocarbons. However, there has been a problem that it is not possible to sufficiently disassemble the device even if it is used.

【0007】本発明は、上述した事情を考慮してなされ
たもので、4環のピレン、5環のベンゾピレンといった
難分解性の多環芳香族炭化水素についても速やかに分解
可能な微生物による汚染物質の分解除去方法及びそれに
用いる汚染物質分解用添加剤を提供することを目的とす
る。
The present invention has been made in view of the above circumstances, and is a microorganism contaminant capable of rapidly decomposing even hardly decomposable polycyclic aromatic hydrocarbons such as 4-ring pyrene and 5-ring benzopyrene. It is an object of the present invention to provide a method for decomposing and removing water and a contaminant decomposition additive used therefor.

【0008】[0008]

【課題を解決するための手段】上記目的を達成するた
め、本発明に係る微生物による汚染物質の分解除去方法
は請求項1に記載したように、所定の堆肥を木質材料で
二次発酵させ、該二次発酵物質を多環芳香族炭化水素又
はそれと構造類似の化合物からなる汚染物質が含まれた
汚染物に添加混合して該汚染物質を微生物分解するもの
である。
In order to achieve the above object, a method for decomposing and removing contaminants by microorganisms according to the present invention comprises subjecting a predetermined compost to secondary fermentation with a woody material. The secondary fermentation substance is added to and mixed with a contaminant containing a contaminant composed of a polycyclic aromatic hydrocarbon or a compound having a structure similar thereto, and the contaminant is decomposed by microorganisms.

【0009】また、本発明に係る微生物による汚染物質
の分解除去方法は、前記汚染物質を、フェナントレン、
アントラセン、フルオランテン、ピレン、クリセン等の
多環芳香族炭化水素としたものである。
Further, the method for decomposing and removing contaminants by microorganisms according to the present invention comprises the steps of:
It is a polycyclic aromatic hydrocarbon such as anthracene, fluoranthene, pyrene and chrysene.

【0010】また、本発明に係る微生物による汚染物質
の分解除去方法は、前記汚染物質を、フェナントレン、
アントラセン、フルオランテン、ピレン、クリセン等の
多環芳香族炭化水素及び脂肪族炭化水素とからなる混合
物としたものである。
In the method for decomposing and removing contaminants by microorganisms according to the present invention, the contaminants may be phenanthrene,
It is a mixture comprising a polycyclic aromatic hydrocarbon such as anthracene, fluoranthene, pyrene, chrysene and the like and an aliphatic hydrocarbon.

【0011】また、本発明に係る微生物による汚染物質
の分解除去方法は、前記堆肥を羊糞堆肥としたものであ
る。
In the method for decomposing and removing contaminants by microorganisms according to the present invention, the compost is a sheep dung compost.

【0012】また、本発明に係る汚染物質分解用添加剤
は請求項5に記載したように、所定の堆肥を木質材料で
二次発酵させてなるものである。
Further, the additive for decomposing pollutants according to the present invention is obtained by subjecting a predetermined compost to secondary fermentation with a woody material.

【0013】本発明に係る微生物による汚染物質の分解
除去方法及びそれに用いる汚染物質分解用添加剤におい
ては、所定の堆肥を使用することを前提とするが、本発
明で言うところの堆肥とは、多環芳香族炭化水素又はそ
れと構造類似の化合物を分解可能な酵素(リグニン分解
酵素と考えられる)を出す微生物はほとんど存在しない
か、存在したとしても酵素活性は低い堆肥、言い換えれ
ば、多環芳香族炭化水素又はそれと構造類似の化合物か
らなる汚染物質に対して分解性を有しない堆肥を意味す
るものとする。したがって、多環芳香族炭化水素又はそ
れと構造類似の化合物からなる汚染物質が含まれた汚染
物に本発明で言うところの堆肥を添加しただけでは、該
汚染物に含まれる上述した汚染物質を確実に分解無害化
することは難しい。
In the method for decomposing and removing contaminants by microorganisms and the additive for decomposing contaminants used therein according to the present invention, it is premised that predetermined compost is used. Almost no microorganisms produce enzymes capable of degrading polycyclic aromatic hydrocarbons or compounds similar in structure to them (considered as lignin-degrading enzymes), or even if present, they have low enzyme activity in compost, in other words, polycyclic aromatics. Compost which does not decompose to pollutants consisting of group hydrocarbons or compounds similar in structure thereto. Therefore, simply adding the compost referred to in the present invention to a contaminant containing a contaminant composed of a polycyclic aromatic hydrocarbon or a compound having a similar structure to the contaminant ensures that the contaminant contained in the contaminant is contained. Detoxification is difficult.

【0014】しかし、本出願人は、牛糞堆肥を用いて多
環芳香族炭化水素を分解することができることを以前に
見いだしており、それを踏まえつつ、他の堆肥を用いて
多環芳香族炭化水素又はそれと構造類似の化合物を分解
できないか、さまざまな実験を繰り返して研究を重ねた
結果、多環芳香族炭化水素等からなる汚染物質に対して
分解性を有しない堆肥であっても、かかる汚染物質を分
解できることを見い出したものである。
However, the present applicant has previously found that polycyclic aromatic hydrocarbons can be decomposed using cow manure compost, and based on this finding, polycyclic aromatic hydrocarbons can be decomposed using other composts. As a result of repeatedly conducting various experiments and studying whether hydrogen or a compound similar in structure cannot be decomposed, even if the compost has no decomposability to pollutants consisting of polycyclic aromatic hydrocarbons, such It has been found that pollutants can be decomposed.

【0015】すなわち、本発明に係る微生物による汚染
物質の分解除去方法及びそれに用いる汚染物質分解用添
加剤においては、まず上述した堆肥を木質材料で二次発
酵させる。
That is, in the method for decomposing and removing contaminants by microorganisms according to the present invention and the additive for decomposing contaminants used therein, first, the above-mentioned compost is secondarily fermented with wood material.

【0016】次に、このように所定の堆肥を木質材料で
二次発酵させた二次発酵物質を多環芳香族炭化水素又は
それと構造類似の化合物からなる汚染物質が含まれた汚
染物に添加混合する。
Next, the secondary fermented substance obtained by subjecting the predetermined compost to secondary fermentation with the woody material is added to the contaminant containing the contaminant composed of the polycyclic aromatic hydrocarbon or a compound similar in structure to the polycyclic aromatic hydrocarbon. Mix.

【0017】このようにすると、二次発酵物質内で増殖
した微生物群は、多環芳香族炭化水素又はそれと構造類
似の化合物からなる汚染物質をすみやかに分解除去す
る。
In this way, the microorganisms proliferated in the secondary fermentation substance immediately decompose and remove polycyclic aromatic hydrocarbons or contaminants composed of compounds similar in structure to the polycyclic aromatic hydrocarbons.

【0018】これは、堆肥に含まれていた微生物のう
ち、木質材料に含まれるリグニンを資化可能な微生物、
いわばリグニン資化菌が木質材料中のリグニンを分解資
化しながら増殖し、次いで、今度は、その増殖したリグ
ニン資化菌がリグニンと構造類似の多環芳香族炭化水素
又はそれと構造類似の化合物を分解するからであると考
えられる。
This is a microorganism capable of assimilating lignin contained in woody material among microorganisms contained in compost,
In other words, the lignin-utilizing bacteria grow while decomposing and assimilating lignin in the woody material, and then, the grown lignin-utilizing bacteria produce polycyclic aromatic hydrocarbons similar in structure to lignin or compounds similar thereto. It is considered that it is decomposed.

【0019】なお、例えば羊糞堆肥が草で発酵させてあ
ることからもわかるように、上述した堆肥は、あらかじ
め木質材料以外の材料で発酵させてあるため、かかる堆
肥を木質材料で発酵させることを、本明細書では特に二
次発酵と呼ぶこととする。
As can be seen from the fact that sheep dung compost is fermented with grass, for example, the above-mentioned compost is previously fermented with a material other than woody material. Is particularly referred to herein as secondary fermentation.

【0020】本発明において分解除去の対象となる汚染
物質は、多環芳香族炭化水素又はそれと構造類似の化合
物である。
In the present invention, the contaminant to be decomposed and removed is a polycyclic aromatic hydrocarbon or a compound similar in structure to the polycyclic aromatic hydrocarbon.

【0021】ここで、多環芳香族炭化水素としては、4
環を含むフルオランテン、ピレン、ベンゾアントラセ
ン、クリセンや、5環を含むベンゾフルオランテン、ベ
ンゾピレンといったいわゆる難分解性多環芳香族炭化水
素が主な対象となるが、フェナントレン、アントラセン
といった3環を含む易分解性の多環芳香族炭化水素やそ
れ以下の多環芳香族炭化水素を排除するものではない。
Here, the polycyclic aromatic hydrocarbon includes 4
So-called hardly decomposable polycyclic aromatic hydrocarbons such as fluoranthene, pyrene, benzoanthracene, and chrysene containing a ring, and benzofluoranthene and benzopyrene containing a five-ring are mainly used, but include three rings such as phenanthrene and anthracene. It does not exclude easily decomposable polycyclic aromatic hydrocarbons or lower polycyclic aromatic hydrocarbons.

【0022】一方、多環芳香族炭化水素と構造類似の化
合物としては、少なくともダイオキシン類及びPCBが
含まれる。
On the other hand, compounds having a structure similar to polycyclic aromatic hydrocarbons include at least dioxins and PCB.

【0023】このように本発明が適用できる汚染物質は
広い範囲に及ぶが、具体的には、上述したように、フェ
ナントレン、アントラセン、フルオランテン、ピレン、
クリセン等の多環芳香族炭化水素を対象とすることが考
えられる。
As described above, the contaminants to which the present invention can be applied cover a wide range. Specifically, as described above, phenanthrene, anthracene, fluoranthene, pyrene,
It is conceivable to target polycyclic aromatic hydrocarbons such as chrysene.

【0024】ここで、このような多環芳香族炭化水素に
加えて脂肪族炭化水素が混在してなる汚染物質を対象と
した場合、脂肪族炭化水素が存在する状況下でも、多環
芳香族炭化水素を速やかに分解除去することが可能とな
り、例えば原油で汚染された油汚染土を処理するのにき
わめて優れた効果を発揮する。
Here, when a pollutant in which an aliphatic hydrocarbon is mixed in addition to such a polycyclic aromatic hydrocarbon is targeted, even if the aliphatic hydrocarbon is present, the polycyclic aromatic hydrocarbon is used. It is possible to quickly decompose and remove hydrocarbons, and it is extremely effective in treating oil-contaminated soil contaminated with crude oil, for example.

【0025】木質材料は、リグニンが含まれていればど
のようなものでもよく、その形態も任意であって例えば
オガクズ状の木質材料を用いることが考えられる。ちな
みに、リグニンは、木材中にセルロースに伴って20〜
30%存在しているため、ほとんどの木材が本発明の木
質材料として使用することができると考えられる。
The wood material may be any material as long as it contains lignin, and may have any form. For example, a sawdust-like wood material may be used. By the way, lignin is 20-
It is believed that most wood can be used as the wood material of the present invention because it is present at 30%.

【0026】汚染物は、多環芳香族炭化水素又はそれと
構造類似の化合物からなる汚染物質が含まれている限
り、該汚染物質がどのようなものに混入しているかは任
意であり、例えば、多環芳香族炭化水素やこれに加えて
脂肪族炭化水素が汚染物質として混入してなる油汚染土
が本発明で言うところの汚染物に該当するほか、プラス
チック廃材、コンクリート廃材といった産業廃棄物等に
上述した汚染物質が混入している場合にも本発明の汚染
物に包摂される。
As long as the contaminant contains a contaminant composed of a polycyclic aromatic hydrocarbon or a compound having a structure similar to the contaminant, the type of the contaminant is arbitrary. Oil-contaminated soil obtained by mixing polycyclic aromatic hydrocarbons and aliphatic hydrocarbons as contaminants in addition to the pollutants referred to in the present invention, industrial waste such as plastic waste, concrete waste, etc. Even when the above-mentioned contaminants are mixed, the contaminants of the present invention are included.

【0027】[0027]

【発明の実施の形態】以下、本発明に係る微生物による
汚染物質の分解除去方法及びそれに用いる汚染物質分解
用添加剤の実施の形態について、添付図面を参照して説
明する。なお、従来技術と実質的に同一の部品等につい
ては同一の符号を付してその説明を省略する。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, embodiments of a method for decomposing and removing contaminants by microorganisms and an additive for decomposing contaminants used in the present invention will be described with reference to the accompanying drawings. It is to be noted that the same reference numerals are given to components and the like that are substantially the same as those in the conventional technology, and description thereof will be omitted.

【0028】本実施形態に係る微生物による汚染物質の
分解除去方法においては、所定の堆肥として羊糞堆肥を
用いるものとし、まず、かかる羊糞堆肥を木質材料で二
次発酵させる。
In the method for decomposing and removing contaminants by microorganisms according to the present embodiment, sheep dung compost is used as a predetermined compost, and the sheep dung compost is secondarily fermented with a woody material.

【0029】木質材料としては、例えばオガクズを用い
ることができる。
As the woody material, for example, sawdust can be used.

【0030】次に、このように羊糞堆肥を木質材料とし
てのオガクズで二次発酵させた二次発酵物質をフェナン
トレン、アントラセン、フルオランテン、ピレン、クリ
セン等の多環芳香族炭化水素(PAH)を汚染物質とし
て含む汚染物としての油汚染土に添加混合する。
Next, the secondary fermentation material obtained by secondary fermentation of sheep dung compost with sawdust as a woody material is converted into polycyclic aromatic hydrocarbons (PAH) such as phenanthrene, anthracene, fluoranthene, pyrene and chrysene. Add to and mix with oil contaminated soil as pollutants including as pollutants.

【0031】このようにすると、二次発酵物質内で増殖
した微生物群は、脂肪族炭化水素が存在するかいなかに
関わらず、一定の多環芳香族炭化水素を速やかに分解す
る。
In this way, the microorganisms proliferated in the secondary fermentation substance rapidly decompose certain polycyclic aromatic hydrocarbons regardless of the presence or absence of aliphatic hydrocarbons.

【0032】これは、羊糞堆肥に含まれていた微生物の
うち、木質材料に含まれるリグニンを資化可能な微生
物、いわばリグニン資化菌が木質材料中のリグニンを分
解資化しながら増殖し、次いで、今度は、その増殖した
リグニン資化菌がリグニンと構造類似の多環芳香族炭化
水素を分解するからであると考えられる。
This is because, among the microorganisms contained in the sheep dung compost, microorganisms capable of assimilating lignin contained in the woody material, that is, lignin-utilizing bacteria grow while decomposing and assimilating lignin in the woody material. Next, it is considered that this time the grown lignin-utilizing bacteria degrade polycyclic aromatic hydrocarbons similar in structure to lignin.

【0033】以上説明したように、本実施形態に係る微
生物による汚染物質の分解除去方法によれば、本来であ
れば、難分解性多環芳香族炭化水素を分解可能な微生物
がほとんど存在しない羊糞堆肥であっても、該羊糞堆肥
を木質材料で二次発酵させることにより、難分解性多環
芳香族炭化水素を分解可能な微生物を増殖させることが
可能となる。
As described above, according to the method for decomposing and removing contaminants by microorganisms according to the present embodiment, sheep that originally have few microorganisms capable of decomposing hardly decomposable polycyclic aromatic hydrocarbons exist. Even in the case of a fecal compost, a microorganism capable of decomposing a hardly decomposable polycyclic aromatic hydrocarbon can be grown by secondary fermenting the sheep feces compost with a wooden material.

【0034】特に、脂肪族炭化水素が存在しない状況で
は、羊糞堆肥だけでも一定の分解作用は期待できるもの
の、脂肪族炭化水素が混在する状況においては、羊糞堆
肥だけでは、難分解性多環芳香族炭化水素を分解するこ
とはほとんど不可能であったが、本実施形態に係る微生
物による汚染物質の分解除去方法によれば、脂肪族炭化
水素が混在する状況であっても、一定の難分解性多環芳
香族炭化水素を速やかに分解することが可能となる。
In particular, in a situation where no aliphatic hydrocarbon is present, a certain decomposition effect can be expected only with the sheep dung compost alone, but in a situation where the aliphatic hydrocarbon is mixed, the sheep dung compost alone is hardly degradable. Although it was almost impossible to decompose the cyclic aromatic hydrocarbon, according to the method for decomposing and removing contaminants by microorganisms according to the present embodiment, even when aliphatic hydrocarbons are mixed, a certain It becomes possible to rapidly decompose the hardly decomposable polycyclic aromatic hydrocarbon.

【0035】本実施形態では特に言及しなかったが、羊
糞堆肥をオガクズ等の木質材料で二次発酵させてなる二
次発酵物質は、これを汚染物に添加することによって上
述した汚染物質を分解することができるので、該二次発
酵物質は、汚染物質分解用添加剤として機能する。
Although not specifically mentioned in the present embodiment, the secondary fermentation material obtained by secondary fermentation of sheep dung compost with woody material such as sawdust is used to add the above-mentioned contaminants to the contaminants. Since it can be degraded, the secondary fermentation material functions as an additive for decomposing pollutants.

【0036】また、本実施形態では、堆肥として羊糞堆
肥を用いたが、本発明の堆肥はかかる種類の堆肥に限定
されるものではなく、多環芳香族炭化水素又はそれと構
造類似の化合物からなる汚染物質に対して分解性を有し
ない堆肥であれば、どのような堆肥でもかまわない。
In this embodiment, sheep manure compost is used as a compost. However, the compost of the present invention is not limited to this type of compost, but may be made of polycyclic aromatic hydrocarbon or a compound having a structure similar to that. Any compost may be used as long as it is not decomposable with respect to the pollutants.

【0037】次に、本実施形態に係る微生物による汚染
物質の分解除去方法及びそれに用いる汚染物質分解用添
加剤の作用を確認するため、羊糞堆肥を木質材料である
オガクズで二次発酵させ、これを多環芳香族炭化水素に
加えて所定期間養生し、その分解経過を計測したので、
かかる実験概要とその計測結果とを以下に説明する。
Next, in order to confirm the method of decomposing and removing contaminants by microorganisms according to the present embodiment and the effect of the contaminant decomposing additive used therein, sheep dung compost was subjected to secondary fermentation with sawdust, which is a woody material. This was added to the polycyclic aromatic hydrocarbon and cured for a predetermined period, and the decomposition process was measured.
The outline of the experiment and the measurement results will be described below.

【0038】(供試堆肥の作製)(Preparation of test compost)

【0039】供試堆肥は、2種類の堆肥を作製した。As the test compost, two types of compost were prepared.

【0040】一つ目の供試堆肥は、まず、羊糞堆肥(c
fu:細菌1.7E+7/g、糸状菌2.4E+6/g)を500mlビ
ーカーに100g採取し、次いで、この中に木質材料で
あるオガクズ10g、米糠1.1g、水道水10ml添
加した後、これを35゜Cで14日間培養して作製した
(以下、これを微生物資材Bと呼ぶ)。
[0040] The first test compost is a sheep dung compost (c).
fu: 1.7E + 7 / g of bacteria and 2.4E + 6 / g of filamentous fungi were collected in a 500 ml beaker, and then 100 g of sawdust, 1.1 g of rice bran, and 10 ml of tap water were added thereto. This was cultured for 14 days at 35 ° C. (hereinafter referred to as microbial material B).

【0041】二つ目の供試堆肥は、同じ羊糞堆肥そのも
のを供試堆肥とした(以下、これを微生物資材Cと呼
ぶ)。
As the second test compost, the same sheep dung compost itself was used as the test compost (hereinafter, this is referred to as microbial material C).

【0042】(実験手順)(Experimental procedure)

【0043】次に、6個の500mlフラスコに海砂1
00gをそれぞれ採取し、これらにアルミ箔でそれぞれ
蓋をした後、乾熱滅菌(170゜C、4時間)した。次
に、かかる6個のフラスコのうち、最初の2個のフラス
コ(フラスコNo.7,10)には、乳鉢で磨砕混合された5
種類の多環芳香族炭化水素(フェナントレン、アントラ
セン、フルオランテン、ピレン、クリセン)だけを50
mgそれぞれ添加し(PAH濃度は5種類で各々100
ppm)、次の2個のフラスコ(フラスコNo.8,11)に
は、脂肪族炭化水素としての潤滑油だけをそれぞれ1g
添加し(脂肪族油分濃度は1%)、最後の2個のフラス
コ(フラスコNo.9,12)には、上述した5種類の多環芳
香族炭化水素と脂肪族炭化水素としての潤滑油の両方を
上述した量だけ同様に添加した。
Next, sea sand 1 was placed in six 500 ml flasks.
Then, 00 g of each sample was collected, each of which was covered with an aluminum foil, and then sterilized by dry heat (170 ° C., 4 hours). Next, of the six flasks, the first two flasks (flasks Nos. 7 and 10) were milled and mixed in a mortar.
50 kinds of polycyclic aromatic hydrocarbons (phenanthrene, anthracene, fluoranthene, pyrene, chrysene)
mg each (PAH concentrations of 5 types and 100
ppm) and the next two flasks (flasks Nos. 8 and 11) each contained only 1 g of lubricating oil as an aliphatic hydrocarbon.
(The concentration of the aliphatic oil is 1%), and the last two flasks (flasks Nos. 9 and 12) contain the above-mentioned five types of polycyclic aromatic hydrocarbons and the lubricating oil as an aliphatic hydrocarbon. Both were similarly added in the amounts described above.

【0044】次に、上述した2種類の微生物資材を微生
物資材Bについては30gずつ、微生物資材Cについて
は7gそれぞれ各フラスコ内に添加するとともに、栄養
塩(滅菌ハイポネックス(商品名)を500倍に希釈し
たもの)を、微生物資材Bについては20ml、微生物
資材Cについては10mlそれぞれ添加した。
Next, 30 g of each of the two types of microbial materials described above was added to each flask for microbial material B, and 7 g of microbial material C was added to each flask, and nutrients (sterilized Hyponex (trade name) were increased by 500 times). 20 ml of the microbial material B and 10 ml of the microbial material C were added.

【0045】次に、各フラスコに100gの砂を入れ、
次いで、開放系養生となるように各フラスコに固めの綿
栓をし、かかる状態で一日に一回の割合で攪拌しつつ、
30゜Cで静置培養し、一定期間経過するまで定期的に
サンプリングして定量分析を行った。なお、静置培養中
は、一週間に一回の割合で蒸散量分だけ水分補給して含
水量を維持するとともに、上述した栄養塩を適宜追加し
た。
Next, put 100 g of sand into each flask,
Then, each of the flasks was hardened with a cotton plug so that it became an open cure, and stirring was performed once a day in such a state,
The culture was allowed to stand at 30 ° C., and periodically sampled until a certain period of time elapses for quantitative analysis. During the stationary culture, the water content was maintained once a week by the amount of transpiration to maintain the water content, and the above-mentioned nutrients were added as appropriate.

【0046】(実験結果)(Experimental results)

【0047】まず、微生物資材Bに対する結果を表1及
び図1に示す。
First, the results for the microbial material B are shown in Table 1 and FIG.

【0048】[0048]

【表1】 [Table 1]

【0049】これらの表及び図でわかるように、微生物
資材Bについては、クリセン以外については、56日経
過を待たずに顕著な分解が進行しているとともに、その
傾向は、PAH単独の場合(同図(a))でも、(PAH
+潤滑油)混合の場合でもほとんど変わらないことがわ
かる。特に、ピレンについては、表1でよくわかるよう
に、(PAH+潤滑油)混在の場合、43.7ppmか
ら56日後には2ppm、112日後には0.5ppm
にまで分解されていることがわかる。
As can be seen from these tables and figures, with respect to the microbial material B, remarkable decomposition progressed without waiting for 56 days except for chrysene, and the tendency was the same as in the case of PAH alone ( (A) in FIG.
+ Lubricant oil) even in the case of mixing. In particular, as can be clearly seen from Table 1, when (PAH + lubricating oil) is mixed, pyrene is 2 ppm from 43.7 ppm after 56 days, and 0.5 ppm after 112 days.
It can be seen that it has been decomposed to.

【0050】したがって、油汚染された土壌を微生物資
材Bで分解除去することは非常に有望であろうと考えら
れる。
Therefore, it is considered very promising to decompose and remove oil-contaminated soil with microbial material B.

【0051】なお、羊糞堆肥だけを用いた供試堆肥、す
なわち微生物資材Cを比較のために表2及び図2に示
す。
A test compost using only sheep manure compost, that is, a microbial material C is shown in Table 2 and FIG. 2 for comparison.

【0052】[0052]

【表2】 [Table 2]

【0053】これらの表及び図でわかるように、羊糞堆
肥だけでも、PAH単独の場合(同図(a))だけで見れ
ば、56日経過の分解経過状況は、微生物資材Bとほと
んど変わりはないが、(PAH+潤滑油)混在の場合
(同図(b))で見れば、PAHの分解は56日経過して
もあまり進んでおらず、難分解性多環芳香族炭化水素を
分解する能力に関する微生物資材Bとの差異は歴然とし
ている。
As can be seen from these tables and figures, the degradation progress after 56 days is almost the same as that of the microbial material B when the sheep dung compost is used alone and when only PAH is used (FIG. (A)). However, in the case of (PAH + lubricating oil) mixture (FIG. (B)), the decomposition of PAH did not progress very much even after 56 days, decomposing the hardly decomposable polycyclic aromatic hydrocarbon. The difference with the microbial material B in the ability to perform is clear.

【0054】この差異は、本来、羊糞堆肥が脂肪族炭化
水素存在下でのPAH分解の進行を促進させる複合系微
生物群を持っていなかったにも関わらず、羊糞堆肥を木
質材料で二次発酵させることにより、かかる複合系微生
物群を獲得できたからであると考えることができる。
[0054] This difference is due to the fact that sheep dung compost is made of wood-based material even though sheep dung compost originally did not have a complex microbial group that promotes the progress of PAH degradation in the presence of aliphatic hydrocarbons. It can be considered that the following fermentation resulted in the acquisition of such a complex microorganism group.

【0055】[0055]

【発明の効果】以上述べたように、本発明に係る微生物
による汚染物質の分解除去方法及びそれに用いる汚染物
質分解用添加剤によれば、本来であれば、多環芳香族炭
化水素又はそれと構造類似の化合物からなる汚染物質を
分解可能な微生物がほとんど存在しない堆肥であって
も、該堆肥を木質材料で二次発酵させることにより、か
かる汚染物質を分解できる微生物を増殖させることが可
能となる。
As described above, according to the method for decomposing and removing contaminants by microorganisms and the contaminant decomposing additive used therein according to the present invention, a polycyclic aromatic hydrocarbon or a polycyclic aromatic hydrocarbon or a polycyclic aromatic hydrocarbon should be used. Even in a compost having almost no microorganisms capable of decomposing contaminants composed of similar compounds, it is possible to proliferate microorganisms capable of decomposing such contaminants by secondary fermenting the compost with woody material. .

【0056】[0056]

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

【図1】本実施形態に係る微生物による汚染物質の分解
除去方法の作用を示したグラフ。
FIG. 1 is a graph showing the operation of a method for decomposing and removing contaminants by microorganisms according to the present embodiment.

【図2】本実施形態に係る微生物による汚染物質の分解
除去方法の作用を示したグラフ。
FIG. 2 is a graph showing the operation of the method for decomposing and removing contaminants by microorganisms according to the embodiment.

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 所定の堆肥を木質材料で二次発酵させ、
該二次発酵物質を多環芳香族炭化水素又はそれと構造類
似の化合物からなる汚染物質が含まれた汚染物に添加混
合して該汚染物質を微生物分解することを特徴とする微
生物による汚染物質の分解除去方法。
Claims: 1. A predetermined compost is secondarily fermented with a woody material,
Adding the secondary fermentation substance to a contaminant containing a contaminant composed of a polycyclic aromatic hydrocarbon or a compound having a structure similar thereto and mixing the contaminant with the contaminant to decompose the contaminant with microorganisms; Decomposition and removal method.
【請求項2】 前記汚染物質を、フェナントレン、アン
トラセン、フルオランテン、ピレン、クリセン等の多環
芳香族炭化水素とした請求項1記載の微生物による汚染
物質の分解除去方法。
2. The method according to claim 1, wherein the contaminants are polycyclic aromatic hydrocarbons such as phenanthrene, anthracene, fluoranthene, pyrene, and chrysene.
【請求項3】 前記汚染物質を、フェナントレン、アン
トラセン、フルオランテン、ピレン、クリセン等の多環
芳香族炭化水素及び脂肪族炭化水素とからなる混合物と
した請求項1記載の汚染物質の分解除去方法。
3. The method for decomposing and removing contaminants according to claim 1, wherein the contaminants are a mixture of polycyclic aromatic hydrocarbons such as phenanthrene, anthracene, fluoranthene, pyrene, chrysene and aliphatic hydrocarbons.
【請求項4】 前記堆肥を羊糞堆肥とした請求項1記載
の微生物による汚染物質の分解除去方法。
4. The method according to claim 1, wherein said compost is sheep dung compost.
【請求項5】 所定の堆肥を木質材料で二次発酵させて
なることを特徴とする汚染物質分解用添加剤。
5. An additive for decomposing pollutants, wherein a predetermined compost is secondarily fermented with a woody material.
JP2000347529A 2000-11-15 2000-11-15 Method for decomposing and removing pollutant by microorganism and additive for decomposition of pollutant to be used for the method Pending JP2002143830A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100656288B1 (en) 2005-01-17 2006-12-11 한국해양연구원 AGENTS FOR ENHANCING BIODEGRADATION RATE OF BENZO[a]PYRENE AND THE METHOD OF BIODEGRADATION WITH SAME
CN103878172A (en) * 2014-04-14 2014-06-25 北京建筑材料科学研究总院有限公司 Method for jointly treating polycyclic aromatic hydrocarbon polluted soil and urban organic waste

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1999055834A1 (en) * 1998-04-28 1999-11-04 Idemitsu Kosan Co., Ltd. Mold capable of degrading dioxin, degradation of dioxin with the use of the same, method for producing composts capable of degrading dioxin and method for growing plants
JP2000107742A (en) * 1998-09-30 2000-04-18 Taisei Corp Method for cleaning of contaminated soil with dioxin
JP2000254635A (en) * 1999-03-05 2000-09-19 Ohbayashi Corp Method of decomposing and removing oil-polluted soil by means of microorganisms, and oil-decomposing additive used in same

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1999055834A1 (en) * 1998-04-28 1999-11-04 Idemitsu Kosan Co., Ltd. Mold capable of degrading dioxin, degradation of dioxin with the use of the same, method for producing composts capable of degrading dioxin and method for growing plants
JP2000107742A (en) * 1998-09-30 2000-04-18 Taisei Corp Method for cleaning of contaminated soil with dioxin
JP2000254635A (en) * 1999-03-05 2000-09-19 Ohbayashi Corp Method of decomposing and removing oil-polluted soil by means of microorganisms, and oil-decomposing additive used in same

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100656288B1 (en) 2005-01-17 2006-12-11 한국해양연구원 AGENTS FOR ENHANCING BIODEGRADATION RATE OF BENZO[a]PYRENE AND THE METHOD OF BIODEGRADATION WITH SAME
CN103878172A (en) * 2014-04-14 2014-06-25 北京建筑材料科学研究总院有限公司 Method for jointly treating polycyclic aromatic hydrocarbon polluted soil and urban organic waste

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