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JP3349433B2 - Organic chlorine compound decomposition treatment method and decomposition treatment device - Google Patents
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JP3349433B2 - Organic chlorine compound decomposition treatment method and decomposition treatment device - Google Patents

Organic chlorine compound decomposition treatment method and decomposition treatment device

Info

Publication number
JP3349433B2
JP3349433B2 JP15528898A JP15528898A JP3349433B2 JP 3349433 B2 JP3349433 B2 JP 3349433B2 JP 15528898 A JP15528898 A JP 15528898A JP 15528898 A JP15528898 A JP 15528898A JP 3349433 B2 JP3349433 B2 JP 3349433B2
Authority
JP
Japan
Prior art keywords
decomposing
active enzyme
mushroom
organic chlorine
dioxins
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.)
Expired - Fee Related
Application number
JP15528898A
Other languages
Japanese (ja)
Other versions
JPH11319786A (en
Inventor
博和 辻
俊也 岡田
英子 大出
源四郎 川合
徳夫 田中
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
Family has litigation
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Application filed by Obayashi Corp filed Critical Obayashi Corp
Priority to JP15528898A priority Critical patent/JP3349433B2/en
Publication of JPH11319786A publication Critical patent/JPH11319786A/en
Application granted granted Critical
Publication of JP3349433B2 publication Critical patent/JP3349433B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
    • 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
    • Y02W30/20Waste processing or separation

Landscapes

  • Fire-Extinguishing Compositions (AREA)
  • Treating Waste Gases (AREA)
  • Processing Of Solid Wastes (AREA)

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、ダイオキシン類を
はじめとした有機塩素化合物の分解処理方法及び分解処
理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and apparatus for decomposing organic chlorine compounds such as dioxins.

【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] Since such bioremediation does not use any chemical agent unlike physical treatment or chemical treatment, it is expected to be low in cost and high in safety, and its application range will be further expanded in the future.

【0005】[0005]

【発明が解決しようとする課題】ところで、有機塩素化
合物の一種であるダイオキシンは、化学物質の製造工程
若しくは塩素処理工程における副産物として生成され、
あるいは廃棄物の燃焼工程において生成される化学物質
であるが、きわめて毒性が強く、環境中に放出された場
合には、環境中で自然に分解されにくいため、生物濃縮
などを経て地球規模で拡散し、生態系に大きな影響を及
ぼすおそれがある。
By the way, dioxin, which is a kind of organochlorine compound, is produced as a by-product in a chemical substance production process or a chlorination process,
Alternatively, it is a chemical substance generated in the process of burning waste, but it is extremely toxic and, when released into the environment, is unlikely to be naturally degraded in the environment. And may have a significant impact on ecosystems.

【0006】そのため、ダイオキシン自体が発生するこ
とがないよう、例えば燃焼炉内では、高い燃焼温度と高
温での十分な滞留時間を保つとともに未然ガスと空気と
を十分に乱流混合させることによってダイオキシン類の
発生を抑制する対策が講じられてはいる。
For this reason, in order to prevent the generation of dioxin itself, for example, in a combustion furnace, a high combustion temperature and a sufficient residence time at a high temperature are maintained, and the gas and air are sufficiently mixed in a turbulent manner. Measures have been taken to control the occurrence of such species.

【0007】しかしながら、例えば土壌に混入する形で
いったん環境に放出されてしまった後では、該土壌内の
ダイオキシンを安全に分離除去する手だてがないのが現
状である。
[0007] However, at present, there is no way to safely separate and remove dioxin from the soil once it has been released into the environment in the form of being mixed into the soil.

【0008】本発明は、上述した事情を考慮してなされ
たもので、環境中に放出されたダイオキシンをはじめと
する有機塩素化合物を分解処理可能な有機塩素化合物の
分解処理方法及び分解処理装置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 provides a method and apparatus for decomposing an organochlorine compound capable of decomposing organic chlorine compounds such as dioxin released into the environment. The purpose is to provide.

【0009】[0009]

【課題を解決するための手段】上記目的を達成するた
め、本発明に係る有機塩素化合物の分解処理方法は請求
項1に記載したように、白色腐朽菌の増殖過程で発生す
る酵素のうち、ダイオキシン類等の有機塩素化合物を分
解可能な活性酵素を有機塩素化合物若しくはそれに汚染
された汚染物質に接触させる有機塩素化合物の分解処理
方法であって、前記活性酵素をきのこ生育用菌床に含有
された形で前記有機塩素化合物若しくはそれに汚染され
た汚染物質に接触させるものである。
Means for Solving the Problems To achieve the above object, the method for decomposing an organochlorine compound according to the present invention comprises, among the enzymes generated during the growth of white rot fungi, A method for decomposing an organic chlorine compound in which an active enzyme capable of decomposing an organic chlorine compound such as dioxins is brought into contact with an organic chlorine compound or a contaminant contaminated with the active enzyme, wherein the active enzyme is contained in a fungal bed for mushroom growth. In contact with the organochlorine compound or contaminants contaminated by it.

【0010】[0010]

【0011】また、本発明に係る有機塩素化合物の分解
処理方法は、前記活性酵素を前記きのこ生育用菌床に含
有された形で前記汚染物質に接触させた後、該きのこ生
育用菌床内に含まれる前記白色腐朽菌の生育に適した条
件で所定期間養生するものである。
In the method for decomposing an organochlorine compound according to the present invention, the active enzyme is brought into contact with the contaminant in a form contained in the mushroom-growing bacterial bed, and then the mushroom-growing bacterial bed is brought into contact with the contaminant. Cured for a predetermined period under conditions suitable for the growth of the white rot fungus contained in the above.

【0012】また、本発明に係る有機塩素化合物の分解
処理方法は、前記養生の際に補給する養分を窒素貧配合
としたものである。
Further, in the method for decomposing an organic chlorine compound according to the present invention, the nutrient to be replenished during the curing is a nitrogen-poor compound.

【0013】また、本発明に係る有機塩素化合物の分解
処理方法は、前記きのこ生育用菌床を、成長したきのこ
を取った後の廃菌床とするものである。
Further, in the method for decomposing an organochlorine compound according to the present invention, the mushroom-growing bacterial bed is a waste bacterial bed after removing the grown mushroom.

【0014】また、本発明に係る有機塩素化合物の分解
処理装置は請求項5に記載したように、白色腐朽菌の増
殖過程で発生する酵素のうち、ダイオキシン類等の有機
塩素化合物を分解可能な活性酵素と有機塩素化合物若し
くはそれに汚染された汚染物質とを中空内部空間にて相
互接触させる密封容器を備え、前記活性酵素をきのこ生
育用菌床に含有された形で前記密封容器内にて遮光状態
で配置するとともに、該密封容器に酸素供給手段、栄養
供給手段及び湿潤手段を設けたものである。
The apparatus for decomposing organic chlorine compounds according to the present invention is capable of decomposing organic chlorine compounds such as dioxins among enzymes generated during the growth of white rot fungi. A sealed container for allowing the active enzyme and the organochlorine compound or the contaminants contaminated by the active enzyme to come into contact with each other in a hollow internal space, wherein the active enzyme is contained in a mushroom growth bacterial bed and is shielded from light in the sealed container. The sealed container is provided with oxygen supply means, nutrient supply means and wetting means.

【0015】[0015]

【0016】請求項1の発明に係る有機塩素化合物の分
解処理方法においては、白色腐朽菌の増殖過程で発生す
る酵素のうち、ダイオキシン類等の有機塩素化合物を分
解可能な活性酵素を有機塩素化合物若しくはそれに汚染
された汚染物質に接触させる。
In the method for decomposing an organochlorine compound according to the first aspect of the present invention, an enzyme capable of decomposing an organochlorine compound such as dioxins among the enzymes generated in the process of growing white rot fungi is used. Or contact with contaminants contaminated by it.

【0017】このようにすると、ダイオキシン類等の有
機塩素化合物は、活性酵素の作用によって水、二酸化炭
素、酸素その他の無害物質に分解される。有機塩素化合
物は、単独の状態でもよいし、土壌、水、空気等に混入
した汚染物質の状態でもよい。
In this manner, organic chlorine compounds such as dioxins are decomposed into water, carbon dioxide, oxygen and other harmless substances by the action of active enzymes. The organic chlorine compound may be in a single state or in a state of a pollutant mixed in soil, water, air, or the like.

【0018】有機塩素化合物としては、ダイオキシン
類、すなわちポリ塩化ジベンゾパラジオキシン(PCDD
s)やポリ塩化ジベンゾフラン(PCDFs)あるいはそれらの
異性体や同族体が主な対象となるが、ここでは、ダイオ
キシンと類似した強い毒性を持つコプラナ―PCB(Co
-PCBs)も含まれる。
The organic chlorine compounds include dioxins, ie, polychlorinated dibenzoparadioxin (PCDD).
s) and polychlorinated dibenzofurans (PCDFs) or their isomers and homologues, but here, coplanar-PCB (Co
-PCBs) are also included.

【0019】白色腐朽菌は木材腐朽菌のうち、セルロー
スとリグニンを分解する菌で、主として担子菌類に属す
る菌である。いずれの白色腐朽菌も使用可能であるが、
シイタケ、マイタケ、ナメコ、エノキタケ、ブナシメ
ジ、キクラゲ等の食用きのこ菌やカワラタケ、スエヒロ
タケ、マンネンタケ等の薬用きのこ菌を用いると、食用
きのこや薬用きのこの生産も兼ねることができ有利であ
る。
The white rot fungi decompose cellulose and lignin among the wood rot fungi and mainly belong to basidiomycetes. Any white rot fungus can be used,
The use of edible mushroom fungi such as shiitake, maitake, nameko, enokitake, bunashimeji, mushroom, etc. and medicinal mushrooms such as kawatake mushroom, suehirotake mushroom, mannentake mushroom, etc., is advantageous because they can double as edible mushrooms and medicinal mushrooms.

【0020】活性酵素をどのような形で利用するかは任
意であって該活性酵素だけを抽出する方法も考えられる
が、活性酵素をきのこ生育用菌床に含有された形で有機
塩素化合物若しくはそれに汚染された汚染物質に接触さ
せるようにすれば、活性酵素だけを抽出する手間やコス
トをかけずとも容易に活性酵素と有機塩素化合物若しく
はその汚染物質とを接触させることができる。
The form in which the active enzyme is used is arbitrary, and a method of extracting only the active enzyme can be considered. However, the active enzyme is contained in the fungal bed for mushroom growth in the form of an organochlorine compound or an organic chlorine compound. By contacting the contaminants with the contaminated contaminants, the active enzymes can be easily brought into contact with the organochlorine compound or the contaminants without the labor and cost of extracting only the active enzymes.

【0021】ここで、きのこ生育用菌床を汚染物質内に
接触させた後、活性酵素によって有機塩素化合物が分解
されるまでの間、特に何の手も加えずに静置して時間経
過を待つようにしてもよいが、該きのこ生育用菌床内に
含まれる前記白色腐朽菌の生育に適した条件、例えば栄
養補給や酸素補給を随時行いつつ、適切な湿度及び遮光
状態を維持した状態で所定期間養生するようにすれば、
当初存在した活性酵素のみならず、あらたに白色腐朽菌
の増殖過程で生成された活性酵素が分解作用に加わるこ
ととなり、分解効率を向上させることができる。
Here, after contacting the fungus bed for growing mushrooms with the contaminant, the organic chloride compound is decomposed by the active enzyme. Although it may be made to wait, conditions suitable for the growth of the white rot fungus contained in the mushroom growth fungus bed, for example, a state where appropriate humidity and light-shielded state are maintained while performing nutritional supplementation and oxygen supplementation as needed If you try to cure for a predetermined period,
Not only the active enzyme present at the beginning, but also the active enzyme newly generated during the growth process of the white rot fungi is added to the decomposition action, and the decomposition efficiency can be improved.

【0022】特に、かかる養生の際に補給する養分を窒
素貧配合としたならば、白色腐朽菌は、有機塩素化合物
を分解するのに寄与する可能性が高いと思われる活性酵
素、例えばリグニン分解酵素を多く生成するので、分解
効率はさらに向上する。
[0022] In particular, if the nutrients supplied during such curing are poor in nitrogen, white rot fungi are likely to contribute to the decomposition of organochlorine compounds, such as active enzymes such as lignin degradation. Since more enzyme is produced, the decomposition efficiency is further improved.

【0023】活性酵素をきのこ生育用菌床に含有された
形で汚染物質内に接触させる場合、活性酵素が白色腐朽
菌から生成されている限り、きのこの培養基質や培養条
件あるいは生育段階とは無関係であってどのようなきの
こ生育用菌床を用いてもよい。例えば白色腐朽菌の菌糸
が十分増殖し活性酵素も十分発現した状態のものを使用
してもよいし、きのこがある程度生育した段階のもので
もよいが、成長したきのこを取り終わった後の廃菌床を
上述のきのこ生育用菌床とするならば、従来であれば廃
棄処分としていた廃培地である廃菌床を有機塩素化合物
の分解除去という用途に再利用することが可能となる。
When the active enzyme is brought into contact with the contaminant in a form contained in the mushroom growth fungal bed, as long as the active enzyme is produced from white-rot fungi, the mushroom culture substrate, culture conditions, or growth stage are as follows. Any mushroom-growing bacterial bed that is irrelevant may be used. For example, it may be used in a state where the hyphae of the white-rot fungi have been sufficiently grown and the active enzyme has been sufficiently expressed, or may be in a stage where the mushrooms have grown to some extent, but the waste bacteria after collecting the grown mushrooms may be used. If the bed is the above-mentioned mushroom-growing bacterial bed, it is possible to reuse the waste bacterial bed, which is a waste medium conventionally discarded, for the purpose of decomposing and removing organic chlorine compounds.

【0024】活性酵素を有機塩素化合物若しくはそれに
汚染された汚染物質に接触させる方法は任意であり、例
えば、活性酵素を含んだきのこ生育用菌床を粉砕してこ
れを有機塩素化合物に汚染された固体である汚染物質に
散布し撹拌混合する方法や、液体である汚染物質に添加
混合する方法、あるいは粉砕物を容器内に充填して該容
器内に液体や気体である汚染物質を流通させるなどの形
態が考えられる。また、活性酵素を含んだ抽出液を有機
塩素化合物に汚染された固体状あるいは液状の汚染物質
に添加する方法や、該抽出液内にガス状の汚染物質を通
す方法などが考えられる。
The method of bringing the active enzyme into contact with the organochlorine compound or a contaminant contaminated with it is optional. For example, a fungus bed for growing mushrooms containing the active enzyme is pulverized and this is contaminated with the organochlorine compound. A method of spraying and stirring and mixing solid contaminants, a method of adding and mixing with liquid contaminants, or a method of filling crushed materials in a container and distributing the liquid or gaseous contaminants in the container. Is possible. Further, a method of adding an extract containing an active enzyme to a solid or liquid contaminant contaminated with an organochlorine compound, a method of passing a gaseous contaminant through the extract, and the like are conceivable.

【0025】請求項5の発明に係る有機塩素化合物の分
解処理装置においては、白色腐朽菌の増殖過程で発生す
る酵素のうち、ダイオキシン類等の有機塩素化合物を分
解可能な活性酵素と有機塩素化合物若しくはそれに汚染
された汚染物質とを密封容器内に入れ、該容器内の中空
空間にて相互に接触させる。
In the apparatus for decomposing an organochlorine compound according to the fifth aspect of the present invention, an active enzyme capable of decomposing an organochlorine compound such as dioxins and an organochlorine compound among enzymes generated during the growth of white rot fungi. Alternatively, the contaminants contaminated with the contaminants are placed in a sealed container and brought into contact with each other in a hollow space in the container.

【0026】このようにすると、ダイオキシン類等の有
機塩素化合物は、活性酵素の作用によって水、二酸化炭
素、酸素その他の無害物質に分解される。
In this way, the organic chlorine compounds such as dioxins are decomposed into water, carbon dioxide, oxygen and other harmless substances by the action of the active enzyme.

【0027】有機塩素化合物や白色腐朽菌の種類、活性
酵素の利用形態、白色腐朽菌の増殖による分解効率の向
上、菌床の種類、活性酵素と有機塩素化合物若しくはそ
れに汚染された汚染物質との接触形態等に関しては、上
述した内容とほぼ同じことが請求項6の発明にも当ては
まり、例えば、活性酵素をきのこ生育用菌床に含有され
た形で密封容器内にて遮光状態で配置するとともに、該
密封容器に酸素供給手段、栄養供給手段及び湿潤手段を
設けるようにしたならば、きのこ生育用菌床内に含まれ
る白色腐朽菌の生育に適した条件、例えば栄養補給及び
酸素補給を随時行いつつ、適当な湿度と遮光状態とを維
持した状態で所定期間養生することが可能となる。した
がって、当初存在する活性酵素のみならず、あらたに白
色腐朽菌の増殖過程で生成される活性酵素が加わること
となり、分解効率を向上させることができる。なお、そ
の他については重複を避けてその説明を省略する。
[0027] Types of organochlorine compounds and white-rot fungi, utilization forms of active enzymes, improvement of decomposition efficiency due to growth of white-rot fungi, types of microbial beds, interaction between active enzymes and organochlorine compounds or contaminants contaminated by them. With respect to the contact form and the like, the same as the contents described above also apply to the invention of claim 6, for example, while arranging the active enzyme in a sealed vessel in a light-shielded state in a form contained in a mushroom growth bacterial bed. If oxygen-supplying means, nutrient-supplying means and wetting means are provided in the sealed container, conditions suitable for the growth of white rot fungi contained in the mushroom-growing fungal bed, such as nutrient replenishment and oxygen replenishment, may be provided at any time. While performing, it is possible to cure for a predetermined period while maintaining appropriate humidity and light-shielded state. Therefore, not only the active enzyme present at the beginning but also the active enzyme generated in the growth process of the white rot fungus is added, and the decomposition efficiency can be improved. The description of the other components is omitted to avoid duplication.

【0028】[0028]

【発明の実施の形態】以下、本発明に係る有機塩素化合
物の分解処理方法及び分解処理装置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。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, embodiments of a method and an apparatus for decomposing an organic chlorine compound according to 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.

【0029】(第1実施形態)本実施形態に係る有機塩
素化合物の分解処理方法は、ダイオキシン類で汚染され
た土壌を現地で分解処理する場合に適用したものであ
り、図1は、その手順について示した工程図である。本
実施形態に係る分解処理方法においては、同図(a)に示
すようにまず、きのこ生育用菌床を予め粉砕して粉砕物
1を製造する。
(First Embodiment) The method for decomposing an organic chlorine compound according to the present embodiment is applied to the case where soil contaminated with dioxins is decomposed on site, and FIG. FIG. In the decomposition treatment method according to the present embodiment, first, as shown in FIG. 1A, a bacterial bed for mushroom growth is pulverized in advance to produce a pulverized material 1.

【0030】ここで、粉砕物1の製造に必要となるきの
こ生育用菌床としては、白色腐朽菌の増殖過程で有機塩
素化合物であるダイオキシン類を分解可能な活性酵素が
菌床内に生成されている必要があるが、かかる菌床は、
通常の食用きのこ類の培養や栽培に用いられている方法
にしたがい、例えば、白色腐朽菌の菌糸をその基質、例
えば、おがくずとふすま等の栄養添加物との混合物を主
体とする培地に生育させれば、該菌床内で白色腐朽菌が
増殖するとともに、それに伴ってダイオキシン類に対し
分解活性を有する活性酵素が菌体外に分泌される。かか
る活性酵素としては、例えばリグニン分解酵素が関わっ
ていると考えられる。
Here, as a fungus bed for mushroom growth necessary for the production of the pulverized material 1, an active enzyme capable of decomposing dioxins, which are organic chlorine compounds, in the growth process of white rot fungi is generated in the fungus bed. It is necessary that
According to the method used for cultivation and cultivation of normal edible mushrooms, for example, the mycelium of white-rot fungi is grown on a substrate thereof, for example, a medium mainly composed of a mixture of nutrient additives such as sawdust and bran. Then, the white rot fungus grows in the bed, and an active enzyme having a decomposing activity for dioxins is secreted out of the cells. As such an active enzyme, for example, lignin-degrading enzyme is considered to be involved.

【0031】なお、かかるきのこ生育用菌床として、活
性酵素が白色腐朽菌から十分に生成されていれば足り、
きのこの成長の程度とは無関係である。したがって、き
のことして成長していないが白色腐朽菌の菌糸の増殖が
ある程度進んだ段階のものや、きのことしてある程度成
長した段階のものなど、さまざまな段階での使用が考え
られるが、リサイクルを考慮すれば、きのこが十分に成
長し、出荷のために摘み取った後のいわゆる廃菌床を用
いるのが好ましい。
It is sufficient that the active enzyme is sufficiently produced from the white rot fungus as such a fungus bed for growing mushrooms.
It has nothing to do with the degree of mushroom growth. Therefore, it can be used at various stages, such as those that have not grown as mushrooms but have grown to some extent, and those that have grown to some extent as mushrooms.However, consider recycling. For example, it is preferable to use a so-called waste bacteria bed after mushrooms have sufficiently grown and picked up for shipping.

【0032】ダイオキシン類には、ポリ塩化ジベンゾパ
ラジオキシン(PCDDs)やポリ塩化ジベンゾフラン(PCDF
s)あるいはそれらの異性体や同族体が含まれる。
Dioxins include polychlorinated dibenzoparadioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs).
s) or their isomers and homologs.

【0033】次に、粉砕物1を同図(b)に示すようにダ
イオキシン類で汚染された汚染物質である汚染土壌2の
表面に散布し、続いて同図(c)に示すように、トラクタ
などを用いて汚染土壌2の表面を耕耘する。そして、き
のこ生育用菌床の粉砕物1を汚染土壌2内に撹拌し、粉
砕物1中の活性酵素と汚染土壌2中のダイオキシン類と
を相互に接触させる。
Next, the pulverized material 1 is sprayed on the surface of the contaminated soil 2 which is a contaminant contaminated with dioxins as shown in FIG. 3B, and then, as shown in FIG. The surface of the contaminated soil 2 is plowed using a tractor or the like. Then, the crushed material 1 of the mushroom-growing bacterial bed is stirred into the contaminated soil 2, and the active enzyme in the crushed material 1 and the dioxins in the contaminated soil 2 are brought into contact with each other.

【0034】次にこれを一定期間静置する。なお、きの
こ生育用菌床の粉砕物1を汚染土壌2に散布してはこれ
を耕耘によって撹拌し、次いで静置するといった一連の
手順を必要に応じて適宜繰り返すようにしてもよい。
Next, this is allowed to stand for a certain period. Note that a series of procedures such as spraying the crushed material 1 of the mushroom-growing bacterial bed onto the contaminated soil 2, stirring the cultivated soil by tillage, and then allowing it to stand still may be repeated as necessary.

【0035】このようにすると、汚染土壌2内のダイオ
キシン類は、それに接触する粉砕物1内の活性酵素の作
用によって水、二酸化炭素、酸素その他の無害物質に分
解される。
In this way, the dioxins in the contaminated soil 2 are decomposed into water, carbon dioxide, oxygen and other harmless substances by the action of the active enzyme in the crushed material 1 that comes into contact therewith.

【0036】以上説明したように、本実施形態に係る有
機塩素化合物の分解処理方法によれば、白色腐朽菌の増
殖過程で発生した活性酵素を利用してダイオキシン類を
無害物質に分解するように構成したので、低コストでし
かも安全性が高いやり方でダイオキシンの分解処理を行
うことが可能となる。
As described above, according to the method for decomposing organochlorine compounds according to the present embodiment, dioxins are decomposed into harmless substances by utilizing active enzymes generated during the growth of white rot fungi. With this configuration, the dioxin can be decomposed in a low-cost and highly safe manner.

【0037】また、本実施形態に係る有機塩素化合物の
分解処理方法によれば、ダイオキシン類に対して分解活
性を有する活性酵素をきのこ生育用菌床の粉砕物1に含
有された形で汚染土壌2に接触させるようにしたので、
活性酵素だけを抽出する手間やコストをかけずとも容易
に活性酵素とダイオキシン類とを接触させて分解を促進
させることができる。
Further, according to the method for decomposing an organic chlorine compound according to the present embodiment, an active enzyme having a decomposing activity for dioxins is contained in a contaminated soil in a form contained in the crushed material 1 of a fungal bed for mushroom growth. Because I contacted 2
The decomposition can be promoted by easily bringing the active enzyme and the dioxins into contact with each other without the trouble and cost of extracting only the active enzyme.

【0038】また、本実施形態に係る有機塩素化合物の
分解処理方法によれば、成長したきのこを摘み取った後
の廃菌床をきのこ生育用菌床としたので、従来であれ
ば、廃棄処分としていた廃菌床をダイオキシン類の分解
処理という用途に再利用することが可能となる。
According to the method for decomposing organochlorine compounds according to the present embodiment, the waste bacterial bed after picking up the grown mushroom is used as a bacterial bed for mushroom growth. It becomes possible to reuse the waste bacteria bed for the purpose of decomposing dioxins.

【0039】(第2実施形態)次に、第2実施形態につ
いて説明する。なお、上述の実施形態と実質的に同一の
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。
(Second Embodiment) Next, a second embodiment will be described. In addition, the same reference numerals are given to components and the like that are substantially the same as those in the above-described embodiment, and description thereof is omitted.

【0040】本実施形態に係る有機塩素化合物の分解処
理方法は、図2に示した工程図でもわかる通り、上述の
実施形態と同様にダイオキシン類で汚染された土壌を現
地で分解処理する場合に適用したものであるが、本実施
形態に係る分解処理方法においては、上述の実施形態と
同様にして製造されたきのこ生育用菌床の粉砕物1を、
同図(a)に示すように養分と水とともにダイオキシン類
で汚染された汚染物質である汚染土壌2の表面に散布
し、続いて同図(b)に示すようにトラクタなどを用いて
汚染土壌2の表面を耕耘撹拌し、粉砕物1中の活性酵素
と汚染土壌2中のダイオキシン類とを相互に接触させ
る。
As can be seen from the process chart shown in FIG. 2, the method for decomposing an organic chlorine compound according to the present embodiment is applicable to the case where soil contaminated with dioxins is decomposed on site similarly to the above-described embodiment. Although applied, in the decomposition treatment method according to the present embodiment, the crushed material 1 of the mushroom-growing bacterial bed manufactured in the same manner as in the above-described embodiment,
As shown in FIG. 3A, the soil and the water are sprayed on the surface of the contaminated soil 2 which is a pollutant contaminated with dioxins, and then, as shown in FIG. The surface of 2 is tilled and stirred, and the active enzyme in the crushed material 1 and the dioxins in the contaminated soil 2 are brought into contact with each other.

【0041】次に、汚染土壌2の上を乾燥防止を兼ねた
遮光性シート11で覆う。なお、きのこ生育用菌床の粉
砕物1を養分や水とともに汚染土壌2に散布してはこれ
を耕耘によって撹拌し、次いで遮光性シート11で覆う
といった一連の手順を必要に応じて適宜繰り返すように
してもよい。
Next, the contaminated soil 2 is covered with a light-shielding sheet 11 which also serves to prevent drying. In addition, a series of procedures, such as spraying the crushed material 1 of the mushroom-growing bacterial bed on the contaminated soil 2 together with nutrients and water, stirring the cultivated soil, and then covering with the light-shielding sheet 11, may be repeated as necessary. It may be.

【0042】このようにすると、汚染土壌2内のダイオ
キシン類は、それに接触する活性酵素の作用によって
水、二酸化炭素、酸素その他の無害物質に分解される。
そして、かかる活性酵素は、養生期間中においても粉砕
物1に含まれる白色腐朽菌の増殖過程であらたに生成さ
れるので、高い効率で分解が行われる。
In this way, the dioxins in the contaminated soil 2 are decomposed into water, carbon dioxide, oxygen and other harmless substances by the action of the active enzyme that comes into contact therewith.
The active enzyme is newly generated during the growth process of the white rot fungus contained in the pulverized material 1 even during the curing period, so that the decomposition is performed with high efficiency.

【0043】以上説明したように、本実施形態に係る有
機塩素化合物の分解処理方法によれば、第1実施形態と
同様、白色腐朽菌の増殖過程で発生した活性酵素を利用
してダイオキシン類を無害物質に分解するように構成し
たので、低コストでしかも安全性が高いやり方でダイオ
キシンの分解処理を行うことが可能となるとともに、ダ
イオキシン類に対して分解活性を有する活性酵素をきの
こ生育用菌床の粉砕物1に含有された形で汚染土壌2に
接触させるようにしたので、活性酵素だけを抽出する手
間やコストをかけずとも容易に活性酵素とダイオキシン
類とを接触させて分解を促進させることが可能となり、
さらに、成長したきのこを摘み取った後の廃菌床をきの
こ生育用菌床としたので、従来であれば、廃棄処分とし
ていた廃菌床をダイオキシン類の分解処理という用途に
再利用することが可能となる。
As described above, according to the method for decomposing organochlorine compounds according to the present embodiment, dioxins can be converted by utilizing active enzymes generated during the growth of white rot fungi, as in the first embodiment. As it is configured to decompose into harmless substances, it is possible to decompose dioxin in a low-cost and highly safe manner, and to use an active enzyme that has decomposing activity on dioxins for mushroom growth. Since the soil contained in the ground material 1 of the floor is brought into contact with the contaminated soil 2, the active enzyme and the dioxins are easily brought into contact with each other to promote the decomposition without the labor and cost of extracting only the active enzyme. It is possible to make
In addition, the waste bacteria bed after picking up the grown mushrooms is used as a mushroom growth bacterial bed, so that waste bacteria beds that had been disposed of in the past can be reused for the purpose of decomposing dioxins. Becomes

【0044】また、本実施形態に係る有機塩素化合物の
分解処理方法によれば、きのこ生育用菌床の粉砕物1を
養分や水とともに汚染土壌2内に加え、しかる後に遮光
性シート11で汚染土壌2の上を覆って養生するように
したので、遮光性シート11の下では、適当な湿度と遮
光状態とが維持されて粉砕物1中の白色腐朽菌が増殖す
るのに適した条件となる。したがって、養生期間中は、
当初存在した活性酵素のみならず、白色腐朽菌の増殖過
程で生成された活性酵素があらたに加わることとなり、
ダイオキシン類の分解効率をさらに向上させることがで
きる。
According to the method for decomposing an organochlorine compound according to the present embodiment, the crushed material 1 of the mushroom-growing bacterial bed is added to the contaminated soil 2 together with nutrients and water. Since the soil is covered and cured, under the light-shielding sheet 11, appropriate humidity and light-shielding state are maintained, and conditions suitable for the growth of white rot bacteria in the crushed material 1 are determined. Become. Therefore, during the curing period,
Not only the active enzyme that originally existed, but also the active enzyme generated during the growth process of the white-rot fungi was added,
The decomposition efficiency of dioxins can be further improved.

【0045】本実施形態では特に言及しなかったが、養
生の際に粉砕物1に加える養分を窒素貧配合としたなら
ば、白色腐朽菌は、ダイオキシン類を分解するのに寄与
する可能性が高いと思われる活性酵素、例えばリグニン
分解酵素を多く生成するので、分解効率はさらに向上す
る。
Although not particularly mentioned in the present embodiment, if the nutrient added to the pulverized material 1 during curing is a poor nitrogen content, the white rot fungi may contribute to decomposing dioxins. Since the active enzyme which is considered to be high, for example, lignin-degrading enzyme is produced in a large amount, the degradation efficiency is further improved.

【0046】また、第1実施形態、第2実施形態では、
いずれもきのこ生育用菌床を粉砕して作った粉砕物1を
現場の汚染土壌2に散布するようにしたが、これに代え
て現場の汚染土壌2をブルドーザ等で剥ぎ取り、これに
粉砕物1を混ぜながら混合して野積みするようにしても
よいし、ブルドーザ等で剥ぎ取った汚染土壌2に粉砕物
1を養分や水とともに混ぜながら混合して野積みし、そ
の上に遮光性シート11を被せて養生するようにしても
よい。
In the first and second embodiments,
In each case, the crushed material 1 made by crushing the fungus bed for mushroom growth was sprayed on the contaminated soil 2 at the site. Instead, the contaminated soil 2 at the site was peeled off with a bulldozer or the like, and the crushed material was added thereto. 1 may be mixed and stacked in a pile, or the contaminated soil 2 peeled off with a bulldozer or the like may be mixed with the nutrients and water while mixing the crushed material 1 with the nutrients or water, and the light-shielding sheet may be placed thereon. You may make it cover 11 and cure.

【0047】(第3実施形態)次に、第3実施形態に係
る有機塩素化合物の分解処理装置を説明する。なお、上
述の実施形態と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。
(Third Embodiment) Next, an apparatus for decomposing an organic chlorine compound according to a third embodiment will be described. Note that the same components and the like as those in the above-described embodiment are denoted by the same reference numerals, and description thereof will be omitted.

【0048】図3は、本実施形態に係る分解処理装置の
全体概略図である。同図でわかるように、本実施形態に
係る有機塩素化合物の分解処理装置21は、有機塩素化
合物であるダイオキシン類で汚染された汚染土壌2が投
入される投入口23が形成された密封容器24を備え、
該密封容器には、ダイオキシン類に対して分解活性を有
する活性酵素が含まれたきのこ育成用菌床を粉砕して得
た粉砕物1を投入する投入口25を設けてある。
FIG. 3 is an overall schematic diagram of the decomposition processing apparatus according to this embodiment. As can be seen from the figure, an organic chlorine compound decomposition treatment apparatus 21 according to the present embodiment includes a sealed container 24 in which an input port 23 into which contaminated soil 2 contaminated with dioxins, which is an organic chlorine compound, is input is formed. With
The sealed container is provided with an inlet 25 into which a crushed product 1 obtained by crushing a mushroom-growing bacterial bed containing an active enzyme having a decomposing activity for dioxins is introduced.

【0049】ここで、密封容器24は、全体が遮光性材
料で形成してあって内部に日光が差し込まないように形
成してあるとともに、その中空内部には汚染土壌2と粉
砕物1とを混合撹拌する撹拌手段としての撹拌スクリュ
ー26が設けてある。また、密封容器24には、酸素供
給手段である酸素供給管27及び栄養供給手段である栄
養補給管28が接続してあり、それぞれの管を介して酸
素と栄養とを密封容器24内の粉砕物1に供給できるよ
うになっているとともに、該容器の内部上方には、湿潤
手段である散水装置29を設けてあり、密封容器24内
に随時水分を供給できるようになっている。
Here, the sealed container 24 is formed entirely of a light-shielding material so as not to allow sunlight to enter therein, and has a contaminated soil 2 and a crushed material 1 in its hollow interior. A stirring screw 26 is provided as stirring means for mixing and stirring. Further, an oxygen supply pipe 27 as an oxygen supply means and a nutrition supply pipe 28 as a nutrition supply means are connected to the sealed container 24, and oxygen and nutrients are pulverized in the sealed container 24 through the respective pipes. The container 1 can be supplied with water, and a watering device 29 as a wetting means is provided above the inside of the container so that water can be supplied into the sealed container 24 at any time.

【0050】本実施形態に係る有機塩素化合物の分解処
理装置21においては、第1実施形態で説明したと同様
にして製造されたきのこ生育用菌床の粉砕物1を投入口
25を介して密封容器24内に投入するとともに、ダイ
オキシン類で汚染された汚染土壌2を投入口23を介し
て密封容器24内に投入する。
In the organic chlorine compound decomposition treatment apparatus 21 according to the present embodiment, the crushed material 1 of the mushroom-growing bacterial bed manufactured in the same manner as described in the first embodiment is sealed through the inlet 25. While being charged into the container 24, the contaminated soil 2 contaminated with dioxins is charged into the sealed container 24 via the charging port 23.

【0051】次に、撹拌スクリュー26を回転駆動して
粉砕物1及び汚染土壌2を混合撹拌し、粉砕物1中の活
性酵素と汚染土壌2中のダイオキシン類とを相互に接触
させる。このとき、粉砕物1の投入とともに該粉砕物中
の白色腐朽菌の増殖に必要な栄養と水を併せて供給す
る。
Next, the stirring screw 26 is driven to rotate, and the pulverized material 1 and the contaminated soil 2 are mixed and stirred, whereby the active enzyme in the pulverized material 1 and the dioxins in the contaminated soil 2 are brought into contact with each other. At this time, nutrients and water necessary for the growth of white rot fungi in the crushed material are supplied together with the addition of the crushed material 1.

【0052】一方、初期投入ないしは初期供給後、栄養
補給管28、散水装置29を介して養分、水を随時補給
とともに、酸素補給管27を介して酸素を随時補給し、
場合によっては、投入口25から粉砕物1を追加投入す
る。そして、これらの補給時、投入時あるいはこれらと
は関係なく随時、撹拌スクリュー26を回転駆動して粉
砕物1中の活性酵素と汚染土壌2中のダイオキシン類と
の接触性を高め、反応を促進させる。
On the other hand, after the initial supply or initial supply, nutrients and water are supplied at any time via the nutrition supply pipe 28 and the watering device 29, and oxygen is supplied at any time via the oxygen supply pipe 27.
In some cases, the pulverized material 1 is additionally supplied from the charging port 25. Then, at the time of replenishment, introduction or at any time irrespective of these, the stirring screw 26 is driven to rotate to increase the contact between the active enzyme in the pulverized material 1 and the dioxins in the contaminated soil 2 to promote the reaction. Let it.

【0053】このようにすると、汚染土壌2内のダイオ
キシン類は、それに接触する活性酵素の作用によって
水、二酸化炭素、酸素その他の無害物質に分解される。
そして、かかる活性酵素は、養生期間中においても粉砕
物1に含まれる白色腐朽菌の増殖過程であらたに生成さ
れるので、高い効率で分解が行われる。
In this manner, dioxins in the contaminated soil 2 are decomposed into water, carbon dioxide, oxygen and other harmless substances by the action of an active enzyme that comes into contact therewith.
The active enzyme is newly generated during the growth process of the white rot fungus contained in the pulverized material 1 even during the curing period, so that the decomposition is performed with high efficiency.

【0054】分解が終了したならば、密封容器24の下
端に設けられた吐出口30から処理済みの土壌を取り出
す。
When the disassembly is completed, the treated soil is taken out from the discharge port 30 provided at the lower end of the sealed container 24.

【0055】以上説明したように、本実施形態に係る有
機塩素化合物の分解処理装置21によれば、白色腐朽菌
の増殖過程で発生した活性酵素を利用してダイオキシン
類を無害物質に分解するように構成したので、低コスト
でしかも安全性が高いやり方でダイオキシンの分解処理
を行うことが可能となるとともに、ダイオキシン類に対
して分解活性を有する活性酵素をきのこ生育用菌床の粉
砕物1に含有された形で汚染土壌2に接触させるように
したので、活性酵素だけを抽出する手間やコストをかけ
ずとも容易に活性酵素とダイオキシン類とを接触させて
分解を促進させることが可能となり、さらに、成長した
きのこを摘み取った後の廃菌床をきのこ生育用菌床とし
たので、従来であれば、廃棄処分としていた廃菌床をダ
イオキシン類の分解処理という用途に再利用することが
可能となる。
As described above, according to the organic chlorine compound decomposing apparatus 21 of the present embodiment, dioxins are decomposed into harmless substances by using active enzymes generated during the growth of white rot fungi. As a result, dioxin can be decomposed in a low-cost and highly safe manner, and an active enzyme having a decomposing activity for dioxins is added to the crushed material 1 of a mushroom-growing bacterial bed. Since it is made to contact the contaminated soil 2 in a contained form, it is possible to easily contact the active enzyme with dioxins to accelerate the decomposition without the labor and cost of extracting only the active enzyme, In addition, the waste bacterial bed after picking up the grown mushrooms was used as a mushroom growth bacterial bed. It is possible to re-use in applications that process.

【0056】また、本実施形態に係る有機塩素化合物の
分解処理装置21によれば、きのこ生育用菌床の粉砕物
1を養分や水とともに汚染土壌2内に加え、しかる後に
遮光性を維持した状態で密封容器24内で養生するよう
にしたので、適当な湿度と遮光状態とが維持されて粉砕
物1中の白色腐朽菌が増殖するのに適した条件となる。
したがって、養生期間中は、当初存在した活性酵素のみ
ならず、白色腐朽菌の増殖過程で生成された活性酵素が
あらたに加わることとなり、ダイオキシン類の分解効率
をさらに向上させることができる。
Further, according to the organochlorine compound decomposing apparatus 21 according to the present embodiment, the crushed material 1 of the mushroom-growing bacterial bed is added to the contaminated soil 2 together with nutrients and water, and thereafter the light-shielding property is maintained. Since the curing is performed in the sealed container 24 in the state, the appropriate humidity and the light-shielding state are maintained, and the condition is suitable for the growth of the white rot bacteria in the crushed material 1.
Therefore, during the curing period, not only the active enzyme originally present but also the active enzyme generated during the growth process of the white rot fungus is newly added, and the decomposition efficiency of dioxins can be further improved.

【0057】(第4実施形態)次に、第4実施形態に係
る有機塩素化合物の分解処理装置を説明する。なお、上
述の実施形態と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。
(Fourth Embodiment) Next, an apparatus for decomposing an organic chlorine compound according to a fourth embodiment will be described. Note that the same components and the like as those in the above-described embodiment are denoted by the same reference numerals, and description thereof will be omitted.

【0058】図4は、本実施形態に係る分解処理装置の
全体概略図である。同図でわかるように、本実施形態に
係る有機塩素化合物の分解処理装置41は、ダイオキシ
ン類に対して分解活性を有する活性酵素が含まれたきの
こ育成用菌床の粉砕物1を充填した密封容器としての浄
化塔42を備え、該浄化塔の下端には、有機塩素化合物
であるダイオキシン類で汚染された汚染物質である汚染
空気を流入させる流入管43が接続してある。かかる流
入管43は、例えば焼却炉の排気ガス管に連結して使用
することができる。
FIG. 4 is an overall schematic diagram of a decomposition processing apparatus according to this embodiment. As can be seen from the figure, the apparatus 41 for decomposing an organochlorine compound according to the present embodiment is sealed and filled with a crushed product 1 of a fungal bed for growing mushrooms containing an active enzyme having a decomposing activity on dioxins. A purifying tower 42 is provided as a container, and an inflow pipe 43 is connected to a lower end of the purifying tower for inflowing polluted air which is a pollutant contaminated with dioxins which are organic chlorine compounds. The inflow pipe 43 can be used, for example, in connection with an exhaust gas pipe of an incinerator.

【0059】ここで、浄化塔42は、全体が遮光性材料
で形成してあって内部に日光が差し込まないように形成
してある。また、浄化塔42には、酸素供給手段である
酸素供給管27及び栄養供給手段である栄養補給管28
が接続してあり、それぞれの管を介して酸素と栄養とを
浄化塔42に充填された粉砕物1に供給できるようにな
っているとともに、該浄化塔の内部上方には、湿潤手段
である散水装置29を設けてあり、浄化塔42内の粉砕
物1に随時水分を供給できるようになっている。
Here, the purification tower 42 is formed entirely of a light-shielding material so that sunlight does not enter inside. Further, the purification tower 42 has an oxygen supply pipe 27 as an oxygen supply means and a nutrition supply pipe 28 as a nutrition supply means.
Are connected so that oxygen and nutrients can be supplied to the pulverized material 1 filled in the purification tower 42 via respective pipes, and a wetting means is provided above the inside of the purification tower. A water sprinkler 29 is provided so that moisture can be supplied to the pulverized material 1 in the purification tower 42 at any time.

【0060】本実施形態に係る有機塩素化合物の分解処
理装置においては、第1実施形態で説明したと同様にし
て製造されたきのこ生育用菌床の粉砕物1を浄化塔42
内に充填し、酸素供給管27、栄養補給管28及び散水
装置29からそれぞれ酸素、栄養、水分を適宜補給する
ことによって粉砕物1中の白色腐朽菌が増殖できる状態
を維持する。
In the apparatus for decomposing organic chlorine compounds according to the present embodiment, the crushed material 1 of the fungal bed for mushroom growth produced in the same manner as described in the first embodiment is used in the purification tower 42.
Then, oxygen, nutrients, and water are appropriately supplied from the oxygen supply pipe 27, the nutrition supply pipe 28, and the sprinkler 29, respectively, to maintain a state in which white rot bacteria in the crushed material 1 can proliferate.

【0061】そして、かかる状態にて流入管43からダ
イオキシン類で汚染された汚染空気を浄化塔42内に流
入させ、粉砕物1中を通過させる。
Then, in this state, the contaminated air contaminated with dioxins flows from the inflow pipe 43 into the purification tower 42 and passes through the pulverized material 1.

【0062】このようにすると、汚染空気内のダイオキ
シン類は、それと接触する粉砕物1中の活性酵素の作用
によって水、二酸化炭素、酸素その他の無害物質に分解
される。そして、かかる活性酵素は、浄化塔42内にお
ける白色腐朽菌の増殖過程でどんどん生成されるので、
汚染空気内のダイオキシン類は、連続的にかつ高い効率
で分解が行われる。
In this way, dioxins in the contaminated air are decomposed into water, carbon dioxide, oxygen and other harmless substances by the action of the active enzyme in the crushed material 1 that comes into contact with the dioxins. And since such active enzyme is generated more and more during the growth process of the white rot fungus in the purification tower 42,
Dioxins in contaminated air are decomposed continuously and with high efficiency.

【0063】分解が終了した空気は、浄化塔42の上方
に設けた放出口44から大気に放出される。
The decomposed air is discharged to the atmosphere from a discharge port 44 provided above the purification tower 42.

【0064】以上説明したように、本実施形態に係る有
機塩素化合物の分解処理装置41によれば、白色腐朽菌
の増殖過程で発生した活性酵素を利用してダイオキシン
類を無害物質に分解するように構成したので、低コスト
でしかも安全性が高いやり方でダイオキシンの分解処理
を行うことが可能となるとともに、ダイオキシン類に対
して分解活性を有する活性酵素をきのこ生育用菌床の粉
砕物1に含有された形で汚染空気に接触させるようにし
たので、活性酵素だけを抽出する手間やコストをかけず
とも容易に活性酵素とダイオキシン類とを接触させて分
解を促進させることが可能となり、さらに、成長したき
のこを摘み取った後の廃菌床をきのこ生育用菌床とした
ので、従来であれば、廃棄処分としていた廃菌床をダイ
オキシン類の分解処理という用途に再利用することが可
能となる。
As described above, according to the organic chlorine compound decomposing apparatus 41 according to the present embodiment, dioxins are decomposed into harmless substances using active enzymes generated during the growth of white rot fungi. As a result, dioxin can be decomposed in a low-cost and highly safe manner, and an active enzyme having a decomposing activity for dioxins is added to the crushed material 1 of a mushroom-growing bacterial bed. Because it was made to contact the contaminated air in the contained form, it is possible to easily contact the active enzyme and dioxins to accelerate the decomposition without the labor and cost of extracting only the active enzyme, and furthermore, The waste bacterial bed after picking up the grown mushrooms was used as a mushroom-growing bacterial bed. It is possible to re-use in applications that sense.

【0065】また、本実施形態に係る有機塩素化合物の
分解処理装置41によれば、きのこ生育用菌床の粉砕物
1が充填された遮光性の浄化塔42内に養分や水を随時
補給するようにしたので、浄化塔42内では、粉砕物1
中の白色腐朽菌が増殖しやすい環境となる。そして、か
かる増殖過程とともにダイオキシン類を分解する活性酵
素もどんどんと菌体外に放出され、かくして、汚染空気
に含まれるダイオキシン類は、浄化塔42内で連続的に
かつ効率よく分解処理することが可能となる。
Further, according to the organic chlorine compound decomposing apparatus 41 according to the present embodiment, nutrients and water are replenished as needed into the light-shielding purification tower 42 filled with the crushed material 1 of the mushroom-growing bacterial bed. Therefore, in the purification tower 42, the crushed material 1
It is an environment where the white rot fungus inside can easily proliferate. And the active enzyme which decomposes dioxins is released rapidly and rapidly with the growth process, and thus the dioxins contained in the contaminated air can be continuously and efficiently decomposed in the purification tower 42. It becomes possible.

【0066】[0066]

【発明の効果】以上述べたように、請求項1に係る本発
明の有機塩素化合物の分解処理方法によれば、低コスト
でしかも安全性が高いやり方でダイオキシンの分解処理
を行うことが可能となるとともに、活性酵素だけを抽出
する手間やコストをかけずとも容易に活性酵素とダイオ
キシン類とを接触させて分解を促進させることができる
という効果も奏する。
As described above, according to the method for decomposing organochlorine compounds of the present invention according to claim 1, it is possible to decompose dioxin in a low cost and highly safe manner. At the same time, there is an effect that the active enzyme and the dioxins can be easily brought into contact with each other to accelerate the decomposition without the labor and cost of extracting only the active enzyme.

【0067】[0067]

【0068】また、請求項2に係る本発明の有機塩素化
合物の分解処理方法によれば、養生期間中は、当初存在
した活性酵素のみならず、白色腐朽菌の増殖過程で生成
された活性酵素があらたに加わることとなり、ダイオキ
シン類の分解効率をさらに向上させることができるとい
う効果も奏する。
According to the method for decomposing organochlorine compounds of the present invention according to the second aspect, during the curing period, not only the active enzyme originally present but also the active enzyme produced during the growth process of the white rot fungus. Is added, and the effect of further improving the decomposition efficiency of dioxins can be obtained.

【0069】また、請求項3に係る本発明の有機塩素化
合物の分解処理方法によれば、白色腐朽菌は、ダイオキ
シン類を分解するのに寄与する可能性が高いと思われる
活性酵素、例えばリグニン分解酵素を多く生成するの
で、分解効率はさらに向上するという効果も奏する。
Further, according to the method for decomposing organochlorine compounds of the present invention according to claim 3, the white rot fungus is considered to have a high possibility of contributing to decompose dioxins, such as lignin. Since a large amount of decomposing enzyme is produced, the effect of further improving the decomposition efficiency is also exerted.

【0070】また、請求項4に係る本発明の有機塩素化
合物の分解処理方法によれば、従来であれば、廃棄処分
としていた廃菌床をダイオキシン類の分解処理という用
途に再利用することが可能となるという効果も奏する。
Further, according to the method for decomposing organic chlorine compounds of the present invention according to claim 4, it is possible to reuse the waste bacteria bed which had been conventionally disposed of for the purpose of decomposing dioxins. It also has the effect that it becomes possible.

【0071】また、請求項5に係る本発明の有機塩素化
合物の分解処理装置によれば、低コストでしかも安全性
が高いやり方でダイオキシンの分解処理を行うことが可
能となるとともに、きのこ生育用菌床内に含まれる白色
腐朽菌の生育に適した条件、例えば栄養補給及び酸素補
給を随時行いつつ、適当な湿度と遮光状態とを維持した
状態で所定期間養生することが可能となる。したがっ
て、当初存在する活性酵素のみならず、あらたに白色腐
朽菌の増殖過程で生成される活性酵素が加わることとな
り、分解効率を向上させることができるという効果も奏
する。
According to the apparatus for decomposing organochlorine compounds of the present invention according to claim 5, it is possible to decompose dioxin in a low-cost and highly safe manner, and at the same time to grow mushrooms. It is possible to cure the white rot fungus contained in the bacterial bed for a predetermined period of time while maintaining appropriate humidity and light-shielding conditions while constantly supplying nutrients and oxygen supplementation as needed. Therefore, not only the active enzyme present at the beginning but also the active enzyme generated in the growth process of the white rot fungus is added, and the effect of improving the decomposition efficiency is also achieved.

【0072】[0072]

【0073】[0073]

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

【図1】第1実施形態に係る有機塩素化合物の分解処理
方法の手順を示した工程図。
FIG. 1 is a process chart showing a procedure of a method for decomposing an organic chlorine compound according to a first embodiment.

【図2】第2実施形態に係る有機塩素化合物の分解処理
方法の手順を示した工程図。
FIG. 2 is a process chart showing a procedure of a method for decomposing an organic chlorine compound according to a second embodiment.

【図3】第3実施形態に係る有機塩素化合物の分解処理
装置の全体断面図。
FIG. 3 is an overall sectional view of an organic chlorine compound decomposition treatment apparatus according to a third embodiment.

【図4】第4実施形態に係る有機塩素化合物の分解処理
装置の全体断面図。
FIG. 4 is an overall sectional view of an organic chlorine compound decomposition treatment apparatus according to a fourth embodiment.

【符号の説明】[Explanation of symbols]

1 きのこ生育用菌床 2 汚染土壌(汚染物質) 11 遮光性シート 21、41 有機塩素化合物の分解処理装置 24 密封容器 27 酸素供給管(酸素供給手段) 28 栄養供給管(栄養供給手段) 29 散水装置(湿潤手段) 42 浄化塔(密封容器) DESCRIPTION OF SYMBOLS 1 Bacterial bed for mushroom growth 2 Contaminated soil (contaminant) 11 Light-shielding sheet 21, 41 Decomposition treatment apparatus for organic chlorine compounds 24 Sealed container 27 Oxygen supply pipe (oxygen supply means) 28 Nutrient supply pipe (nutrition supply means) 29 Watering Equipment (wetting means) 42 Purification tower (sealed vessel)

───────────────────────────────────────────────────── フロントページの続き (72)発明者 大出 英子 東京都清瀬市下清戸4丁目640 株式会 社大林組技術研究所内 (72)発明者 川合 源四郎 群馬県桐生市西久方町1丁目2―23 森 産業株式会社内 (72)発明者 田中 徳夫 群馬県桐生市西久方町1丁目2―23 森 産業株式会社内 (56)参考文献 特開 平6−91290(JP,A) 特開 平9−224657(JP,A) 特開 平10−323646(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01D 53/00 - 53/96 C02F 3/00 - 3/34 B09B 3/00 - 5/00 B09C 1/00 - 1/10 A62D 3/00 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Eiko Oide 4-640 Shimoseito, Kiyose-shi, Tokyo Inside Obayashi Corporation Technical Research Institute (72) Inventor Genshiro Kawai 1-2-23 Nishikugatacho, Kiryu-shi, Gunma Mori Sangyo (72) Inventor Tokuo Tanaka 1-2-23 Nishikugatacho, Kiryu-shi, Gunma Mori Sangyo Co., Ltd. (56) References JP-A-6-91290 (JP, A) JP-A-9-224657 (JP , A) JP-A-10-323646 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) B01D 53/00-53/96 C02F 3/00-3/34 B09B 3/00 -5/00 B09C 1/00-1/10 A62D 3/00

Claims (5)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 白色腐朽菌の増殖過程で発生する酵素の
うち、ダイオキシン類等の有機塩素化合物を分解可能な
活性酵素を有機塩素化合物若しくはそれに汚染された汚
染物質に接触させる有機塩素化合物の分解処理方法であ
って、前記活性酵素をきのこ生育用菌床に含有された形
で前記有機塩素化合物若しくはそれに汚染された汚染物
質に接触させることを特徴とする有機塩素化合物の分解
処理方法。
1. Decomposition of an organochlorine compound by bringing an active enzyme capable of decomposing an organochlorine compound such as dioxins into contact with an organochlorine compound or a pollutant contaminated by the enzyme, among enzymes generated during the growth of white rot fungi. A method for treating an organic chlorine compound, wherein the active enzyme is brought into contact with the organic chlorine compound or a contaminant contaminated by the active chlorine compound in a form contained in a fungus bed for mushroom growth.
【請求項2】 前記活性酵素を前記きのこ生育用菌床に
含有された形で前記汚染物質に接触させた後、該きのこ
生育用菌床内に含まれる前記白色腐朽菌の生育に適した
条件で所定期間養生する請求項1記載の有機塩素化合物
の分解処理方法。
2. A condition suitable for the growth of the white-rot fungi contained in the mushroom-growing bacterial bed after the active enzyme is brought into contact with the contaminant in a form contained in the mushroom-growing bacterial bed. The method for decomposing an organic chlorine compound according to claim 1, wherein the curing is performed for a predetermined period.
【請求項3】 前記養生の際に補給する養分を窒素貧配
合とした請求項2記載の有機塩素化合物の分解処理方
法。
3. The method for decomposing organochlorine compounds according to claim 2, wherein the nutrients to be replenished at the time of curing are a nitrogen-poor compound.
【請求項4】 前記きのこ生育用菌床を、成長したきの
こを取った後の廃菌床とする請求項1記載の有機塩素化
合物の分解処理方法。
4. The method for decomposing an organochlorine compound according to claim 1, wherein the mushroom-growing bacterial bed is a waste bacterial bed after removing the grown mushroom.
【請求項5】 白色腐朽菌の増殖過程で発生する酵素の
うち、ダイオキシン類等の有機塩素化合物を分解可能な
活性酵素と有機塩素化合物若しくはそれに汚染された汚
染物質とを中空内部空間にて相互接触させる密封容器を
備え、前記活性酵素をきのこ生育用菌床に含有された形
で前記密封容器内にて遮光状態で配置するとともに、該
密封容器に酸素供給手段、栄養供給手段及び湿潤手段を
設けたことを特徴とする有機塩素化合物の分解処理装
置。
5. Among the enzymes generated during the growth process of white rot fungi, an active enzyme capable of decomposing an organic chlorine compound such as dioxins and an organic chlorine compound or a pollutant contaminated by the organic chlorine compound are exchanged in a hollow internal space. A sealed container to be contacted is provided, and the active enzyme is arranged in the sealed container in a light-shielded state so as to be contained in a mushroom-growing fungal bed. An organic chlorine compound decomposition treatment apparatus, which is provided.
JP15528898A 1998-05-20 1998-05-20 Organic chlorine compound decomposition treatment method and decomposition treatment device Expired - Fee Related JP3349433B2 (en)

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Application Number Priority Date Filing Date Title
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JP3349433B2 true JP3349433B2 (en) 2002-11-25

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4630427B2 (en) * 2000-07-04 2011-02-09 株式会社大林組 Pollutant treatment method
JP2003275735A (en) * 2002-03-22 2003-09-30 Ohbayashi Corp Hazardous chemical processing equipment
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Also Published As

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