JP2002018425A - Method for treating pollutant - Google Patents
Method for treating pollutantInfo
- Publication number
- JP2002018425A JP2002018425A JP2000202099A JP2000202099A JP2002018425A JP 2002018425 A JP2002018425 A JP 2002018425A JP 2000202099 A JP2000202099 A JP 2000202099A JP 2000202099 A JP2000202099 A JP 2000202099A JP 2002018425 A JP2002018425 A JP 2002018425A
- Authority
- JP
- Japan
- Prior art keywords
- bacterial bed
- contaminated soil
- bed
- pollutant
- soil
- 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.)
- Granted
Links
- 238000000034 method Methods 0.000 title claims abstract description 12
- 239000003344 environmental pollutant Substances 0.000 title abstract description 16
- 231100000719 pollutant Toxicity 0.000 title abstract description 16
- 230000001580 bacterial effect Effects 0.000 claims abstract description 39
- 239000002689 soil Substances 0.000 claims abstract description 37
- 239000002344 surface layer Substances 0.000 claims abstract description 11
- 239000002699 waste material Substances 0.000 claims abstract description 6
- 239000000356 contaminant Substances 0.000 claims description 11
- 238000005507 spraying Methods 0.000 claims description 5
- 238000002156 mixing Methods 0.000 claims description 3
- 238000003756 stirring Methods 0.000 claims description 2
- 241000233866 Fungi Species 0.000 description 6
- 239000000126 substance Substances 0.000 description 4
- 235000001674 Agaricus brunnescens Nutrition 0.000 description 3
- 102000004190 Enzymes Human genes 0.000 description 3
- 108090000790 Enzymes Proteins 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 description 2
- FMMWHPNWAFZXNH-UHFFFAOYSA-N Benz[a]pyrene Chemical compound C1=C2C3=CC=CC=C3C=C(C=C3)C2=C2C3=CC=CC2=C1 FMMWHPNWAFZXNH-UHFFFAOYSA-N 0.000 description 2
- MWPLVEDNUUSJAV-UHFFFAOYSA-N anthracene Chemical compound C1=CC=CC2=CC3=CC=CC=C3C=C21 MWPLVEDNUUSJAV-UHFFFAOYSA-N 0.000 description 2
- 230000000813 microbial effect Effects 0.000 description 2
- 150000004045 organic chlorine compounds Chemical class 0.000 description 2
- YNPNZTXNASCQKK-UHFFFAOYSA-N phenanthrene Chemical compound C1=CC=C2C3=CC=CC=C3C=CC2=C1 YNPNZTXNASCQKK-UHFFFAOYSA-N 0.000 description 2
- 238000010298 pulverizing process Methods 0.000 description 2
- BBEAQIROQSPTKN-UHFFFAOYSA-N pyrene Chemical compound C1=CC=C2C=CC3=CC=CC4=CC=C1C2=C43 BBEAQIROQSPTKN-UHFFFAOYSA-N 0.000 description 2
- 230000002195 synergetic effect Effects 0.000 description 2
- 238000004056 waste incineration Methods 0.000 description 2
- 101100325793 Arabidopsis thaliana BCA2 gene Proteins 0.000 description 1
- 241000894006 Bacteria Species 0.000 description 1
- CYTYCFOTNPOANT-UHFFFAOYSA-N Perchloroethylene Chemical group ClC(Cl)=C(Cl)Cl CYTYCFOTNPOANT-UHFFFAOYSA-N 0.000 description 1
- XSTXAVWGXDQKEL-UHFFFAOYSA-N Trichloroethylene Chemical group ClC=C(Cl)Cl XSTXAVWGXDQKEL-UHFFFAOYSA-N 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- -1 aromatic carbohydrates Chemical class 0.000 description 1
- 235000014633 carbohydrates Nutrition 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 150000002013 dioxins Chemical class 0.000 description 1
- GVEPBJHOBDJJJI-UHFFFAOYSA-N fluoranthrene Natural products C1=CC(C2=CC=CC=C22)=C3C2=CC=CC3=C1 GVEPBJHOBDJJJI-UHFFFAOYSA-N 0.000 description 1
- 230000002538 fungal effect Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 239000000758 substrate Substances 0.000 description 1
- 229950011008 tetrachloroethylene Drugs 0.000 description 1
- UBOXGVDOUJQMTN-UHFFFAOYSA-N trichloroethylene Natural products ClCC(Cl)Cl UBOXGVDOUJQMTN-UHFFFAOYSA-N 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Abstract
Description
【0001】[0001]
【発明の属する技術分野】この発明は、汚染土壌に含ま
れて環境に悪影響を及ぼす難分解性汚染物質を分解処理
する汚染物質処理方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating pollutants which decomposes hard-to-degrade pollutants contained in contaminated soil and adversely affecting the environment.
【0002】[0002]
【従来の技術】近年、廃棄物焼却場の近辺土壌が、焼却
灰に含まれるダイオキシン、トリクロロエチレン、テト
ラクロロエチレン等の有機塩素系化合物で汚染されてい
るとして大きな社会問題となっている。また、有機塩素
系化合物のほか、基板洗浄用溶剤、ベンゾピレン等の芳
香族炭水化物や、水銀系物質等の難分解性物質である汚
染物質により土壌が汚染されているとして問題となって
いるところもある。2. Description of the Related Art In recent years, soil near a waste incineration plant has become a major social problem because it is contaminated with organochlorine compounds such as dioxin, trichloroethylene and tetrachloroethylene contained in incineration ash. In addition to organic chlorine compounds, solvents for cleaning substrates, aromatic carbohydrates such as benzopyrene, and other substances that are contaminated with contaminants that are hardly decomposable substances, such as mercury substances, have also caused problems. is there.
【0003】この問題に取り組むにあたり、本発明者ら
は、キノコ類、例えば白色腐朽菌類を植菌してその菌糸
を生育させるためにオガクズ、培地添加物および水を混
合した菌床を、上記汚染物質やそれら汚染物質を含む汚
染土に混ぜ込むと、発育する菌糸と、菌が発生する分解
酵素との相乗効果により上記汚染物質が分解されるとい
う事実を知見した。なお、本明細書では食用キノコを植
菌・育成するための菌床を特に食用菌菌床と称する。ま
た、本発明者らは、上記菌床で成長したキノコを採取し
おわった利用済みの菌床であって、従来は廃棄されてき
た廃菌床を上記汚染物質や汚染土に混ぜた場合にも、同
様に汚染物質が分解されることも知見した。[0003] In addressing this problem, the present inventors have developed a bacterial bed containing a mixture of sawdust, medium additives and water in order to inoculate mushrooms, for example, white-rot fungi, and to grow their hyphae. It has been found that when mixed with contaminated soil containing substances or contaminants, the contaminants are decomposed by the synergistic effect of the growing mycelium and the decomposing enzyme generated by the fungi. In this specification, a bacterial bed for inoculating and growing edible mushrooms is particularly referred to as an edible bacterial bed. In addition, the present inventors have collected used mushrooms grown on the above-mentioned fungus bed, and used the fungus bed, which was conventionally discarded when the waste fungus bed was mixed with the contaminants or contaminated soil. Also found that pollutants were similarly degraded.
【0004】そこで、これら食用菌菌床および廃菌床等
の菌床を粉砕し、大型機械を用いてこの粉砕物を汚染土
壌に混合して静置することにより汚染物質を処理するこ
とが考えられる。[0004] Therefore, it is conceivable to treat the contaminants by pulverizing the bacterium beds such as the edible microbial bed and the waste microbial bed, and mixing and pulverizing the pulverized material with the contaminated soil using a large-sized machine. Can be
【0005】[0005]
【発明が解決しようとする課題】しかし、従来のような
大型機械を用いた方法においては、汚染土壌全体に対し
て菌床を混合するので、大量の菌床を土壌に混合しなけ
ればならなかった。また、大型の機械を用いて汚染土壌
を撹拌混合した場合、汚染された土が周囲に飛散してし
まうという問題もあった。However, in the conventional method using a large machine, a bacterial bed is mixed with the entire contaminated soil, so that a large amount of the bacterial bed must be mixed with the soil. Was. Further, when the contaminated soil is stirred and mixed using a large-sized machine, there is a problem that the contaminated soil is scattered around.
【0006】ところで、ダイオキシン類にみられるよう
に、多くの汚染物質は疎水性が高いため、ほとんどのも
のは土壌の深層まで浸透せず表層付近に留まっているこ
とが分かった。このことより、従来のように汚染土壌全
体に大量の菌床を混合する必要はなく、土壌の表層にの
み添加すればよいことが判明した。By the way, as seen in dioxins, many contaminants have high hydrophobicity, and it has been found that most contaminants do not penetrate deep into the soil but remain near the surface. From this, it became clear that it was not necessary to mix a large amount of bacterial beds into the entire contaminated soil as in the prior art, and it was only necessary to add it to the surface layer of the soil.
【0007】そこで本発明は、大量の菌床を必要とせ
ず、また、汚染土を周囲に飛散させることなく汚染物質
を分解処理することのできる汚染物質処理方法を提供す
ることを目的とする。Accordingly, an object of the present invention is to provide a pollutant treatment method capable of decomposing a pollutant without requiring a large amount of bacterial beds and without scattering contaminated soil around.
【0008】[0008]
【課題を解決するための手段】本発明は、汚染土壌に対
し、菌床またはその粉砕物を所定の深さ、例えば地表か
ら5cm〜30cm、好ましくは15cm〜25cmま
で挿入するか、あるいは菌床の溶解液を撒布または注入
すると同時に、またはその後、この土壌の表層のみ、例
えば地表から5cm〜30cm、好ましくは15cm〜
25cmを撹拌して前記菌床を汚染土壌中へ混入するこ
とによる汚染物質処理方法を提案する。また、この方法
において、前記菌床は食用菌菌床または廃菌床であって
もよい。According to the present invention, there is provided a method for inserting a fungus bed or a crushed product thereof into a contaminated soil to a predetermined depth, for example, 5 cm to 30 cm, preferably 15 cm to 25 cm from the ground surface, or At the same time as or after spraying or injecting the dissolving solution of the above, only the surface layer of this soil, for example, 5 cm to 30 cm, preferably 15 cm to
We propose a method for treating pollutants by mixing the bacterial bed into contaminated soil by stirring 25 cm. In this method, the bacterial bed may be an edible bacterial bed or a waste bacterial bed.
【0009】[0009]
【発明の実施の形態】以下、本発明の汚染物質処理方法
の一実施形態について説明する。まず、汚染物質処理能
力のある菌床(食用菌菌床または廃菌床)を粉砕して粉
体状にしておく。そしてこの粉体菌床1を図1に示すよ
うな装置Mのトレーラー部2に充填し、このトレーラー
部2に設けた撒布口3から、例えば廃棄物焼却場付近の
汚染物質を含む汚染土壌の表層上に粉体菌床1を撒布す
る。そしてこの撒布作業と同時に、トレーラー部2に取
り付けた小型のプラウ4を用いて撒布した粉体菌床1を
土壌の表層部に鋤込む。この際、汚染土が周囲に飛散し
ないように鋤込み作業をおこなう。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS One embodiment of the method for treating pollutants of the present invention will be described below. First, a bacterial bed (edible bacterial bed or waste bacterial bed) capable of treating contaminants is pulverized into powder. Then, the powdered bacterial bed 1 is filled in a trailer unit 2 of an apparatus M as shown in FIG. 1, and a spout 3 provided in the trailer unit 2 is used to remove contaminated soil containing contaminants near a waste incineration plant, for example. The powdered bacterial bed 1 is spread on the surface layer. Simultaneously with this spraying operation, the powdered bacterial bed 1 sprayed using the small plows 4 attached to the trailer unit 2 is thrown into the surface layer of the soil. At this time, plowing work is performed so that the contaminated soil does not fly around.
【0010】数週間経過すると、鋤込んだ菌床から菌糸
が成長するとともに、この増殖過程で分解酵素が発生す
る。そして成長した菌糸と分解酵素との相乗効果によ
り、汚染土壌の表層に存在する汚染物質が分解され無害
化される。例えば、アントラセン、ピレン、フェナント
レンであれば1ヶ月で200ppmが90%減少し、ベ
ンツピレンであれば60%減少する。ダイオキシンに関
しては20000pgTEQ/gが2ヶ月で60%程度減少す
る。[0010] After several weeks, hyphae grow from the plowed fungal bed, and decomposing enzymes are generated during this growth process. The contaminants present on the surface of the contaminated soil are decomposed and made harmless by the synergistic effect of the grown mycelium and the decomposing enzyme. For example, in the case of anthracene, pyrene and phenanthrene, 200 ppm is reduced by 90% in one month, and in case of benzpyrene, it is reduced by 60%. For dioxin, 20,000 pgTEQ / g is reduced by about 60% in 2 months.
【0011】なお、粉体菌床を汚染土壌に鋤込んだ後、
菌糸が土壌中で成長した時期、例えば撒布後1ヶ月頃に
再度鋤込み作業をおこなえば、菌糸を土壌中に満遍なく
分布させることができ、汚染物質の分解処理をさらに促
進することができる。[0011] After plowing the powdered bacterial bed into the contaminated soil,
If the plowing operation is performed again at the time when the hypha grows in the soil, for example, about one month after the application, the mycelium can be evenly distributed in the soil, and the decomposition treatment of the pollutant can be further promoted.
【0012】上記実施形態では、図1に示すような装置
Mの撒布口3から粉体菌床を撒布する構成について説明
したが、菌床を土壌表層上に撒布することのできる手段
であればどのようなものを使用してもよい。In the above-described embodiment, the structure in which the powdered bacterial bed is sprayed from the spraying port 3 of the apparatus M as shown in FIG. 1 has been described. However, any means capable of spraying the bacterial bed on the surface of the soil can be used. Any one may be used.
【0013】また、撒布した菌床を鋤込むためにプラウ
4を使用することとしたが、実際には菌床を土壌表層部
に鋤込むことのできる手段であればどのようなものを用
いてもよい。さらに、上記実施形態では粉体状に粉砕し
た菌床を撒布することとしたが、菌床を溶解した溶解液
を汚染土壌上に撒布または注入してもよい。Although the plows 4 are used for plowing the scattered bacterial bed, actually, any means can be used as long as the bacterial bed can be plowed into the surface layer of the soil. Is also good. Further, in the above-described embodiment, the bacterial bed crushed into a powder is sprayed. However, a solution in which the bacterial bed is dissolved may be sprayed or injected onto the contaminated soil.
【0014】[0014]
【発明の効果】汚染物質分解能力を有する菌床を汚染土
壌の表層上だけに撒布し、撒布した菌床を土壌表層部に
鋤込むという構成によれば、大型の機械を用いる必要が
ないので、汚染土を周囲に飛散させることなく汚染物質
を効果的に分解処理することができる。また、菌床を汚
染土壌の表層上だけに撒布する構成としたので、菌床の
量は少なくて済み、作業が簡単になる。According to the structure in which the bacterial bed having the ability to decompose pollutants is sprayed only on the surface layer of the contaminated soil and the sprayed bacterial bed is plowed into the surface layer of the soil, it is not necessary to use a large-sized machine. In addition, the pollutants can be effectively decomposed without scattering the contaminated soil to the surroundings. Also, since the bacterial bed is sprayed only on the surface layer of the contaminated soil, the amount of the bacterial bed can be reduced and the operation can be simplified.
【図1】本発明の汚染物質処理方法の一実施形態を示す
概略図である。FIG. 1 is a schematic view showing one embodiment of a pollutant treatment method of the present invention.
1 粉体菌床 2 トレーラー部 3 撒布口 4 プラウ DESCRIPTION OF SYMBOLS 1 Powder bed 2 Trailer part 3 Spray port 4 Plow
───────────────────────────────────────────────────── フロントページの続き (72)発明者 辻 博和 東京都清瀬市下清戸4丁目640番地 株式 会社大林組技術研究所内 Fターム(参考) 4B065 AA57X AC20 BC31 BC50 CA56 4D004 AA41 AB03 AB05 AB06 AB07 AC07 CA15 CA18 CA50 CC07 ────────────────────────────────────────────────── ─── Continuing on the front page (72) Inventor Hirokazu Tsuji 4-640 Shimoseito, Kiyose-shi, Tokyo F-term in Obayashi Corporation Technical Research Institute Co., Ltd. 4B065 AA57X AC20 BC31 BC50 CA56 4D004 AA41 AB03 AB05 AB06 AB07 AC07 CA15 CA18 CA50 CC07
Claims (2)
を所定の深さまで挿入するか、あるいは菌床の溶解液を
撒布または注入すると同時に、またはその後、この土壌
の表層のみを撹拌して前記菌床を汚染土壌中へ混入する
ことを特徴とする汚染物質処理方法。1. Inserting a bacterial bed or a crushed product thereof to a predetermined depth into a contaminated soil, or simultaneously spraying or injecting a solution of the bacterial bed, or thereafter, stirring only the surface layer of the soil. A method for treating contaminants, comprising mixing the bacterial bed into contaminated soil.
あることを特徴とする請求項1に記載の汚染物質処理方
法。2. The method according to claim 1, wherein the bacterial bed is an edible bacterial bed or a waste bacterial bed.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
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JP2000202099A JP4630427B2 (en) | 2000-07-04 | 2000-07-04 | Pollutant treatment method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000202099A JP4630427B2 (en) | 2000-07-04 | 2000-07-04 | Pollutant treatment method |
Publications (2)
Publication Number | Publication Date |
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JP2002018425A true JP2002018425A (en) | 2002-01-22 |
JP4630427B2 JP4630427B2 (en) | 2011-02-09 |
Family
ID=18699672
Family Applications (1)
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JP2000202099A Expired - Fee Related JP4630427B2 (en) | 2000-07-04 | 2000-07-04 | Pollutant treatment method |
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JP (1) | JP4630427B2 (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106180162A (en) * | 2016-07-27 | 2016-12-07 | 广东开源环境科技有限公司 | A kind of deep subsoil blender |
CN112893450A (en) * | 2021-01-13 | 2021-06-04 | 山东海普欧环保设备科技有限公司 | Heavy metal contaminated soil microorganism repair equipment |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH11128903A (en) * | 1997-10-31 | 1999-05-18 | Ohbayashi Corp | Decomposition removal of oil-polluted soil by microorganism |
JPH11319786A (en) * | 1998-05-20 | 1999-11-24 | Ohbayashi Corp | Method and apparatus for decomposition treatment of organochlorine compound |
JP2000107742A (en) * | 1998-09-30 | 2000-04-18 | Taisei Corp | Method for cleaning of contaminated soil with dioxin |
JP2000167532A (en) * | 1998-12-03 | 2000-06-20 | Yukiguni Maitake Co Ltd | Decomposition of harmful environmental pollutant using edible mushroom |
-
2000
- 2000-07-04 JP JP2000202099A patent/JP4630427B2/en not_active Expired - Fee Related
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH11128903A (en) * | 1997-10-31 | 1999-05-18 | Ohbayashi Corp | Decomposition removal of oil-polluted soil by microorganism |
JPH11319786A (en) * | 1998-05-20 | 1999-11-24 | Ohbayashi Corp | Method and apparatus for decomposition treatment of organochlorine compound |
JP2000107742A (en) * | 1998-09-30 | 2000-04-18 | Taisei Corp | Method for cleaning of contaminated soil with dioxin |
JP2000167532A (en) * | 1998-12-03 | 2000-06-20 | Yukiguni Maitake Co Ltd | Decomposition of harmful environmental pollutant using edible mushroom |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106180162A (en) * | 2016-07-27 | 2016-12-07 | 广东开源环境科技有限公司 | A kind of deep subsoil blender |
CN112893450A (en) * | 2021-01-13 | 2021-06-04 | 山东海普欧环保设备科技有限公司 | Heavy metal contaminated soil microorganism repair equipment |
Also Published As
Publication number | Publication date |
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JP4630427B2 (en) | 2011-02-09 |
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