JP2002018424A - Method for treating pollutant - Google Patents
Method for treating pollutantInfo
- Publication number
- JP2002018424A JP2002018424A JP2000201336A JP2000201336A JP2002018424A JP 2002018424 A JP2002018424 A JP 2002018424A JP 2000201336 A JP2000201336 A JP 2000201336A JP 2000201336 A JP2000201336 A JP 2000201336A JP 2002018424 A JP2002018424 A JP 2002018424A
- Authority
- JP
- Japan
- Prior art keywords
- bacterial bed
- soil
- bed
- force
- bacterial
- 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
Links
- 238000000034 method Methods 0.000 title claims abstract description 16
- 239000003344 environmental pollutant Substances 0.000 title claims abstract description 9
- 231100000719 pollutant Toxicity 0.000 title claims abstract description 9
- 230000001580 bacterial effect Effects 0.000 claims abstract description 48
- 239000002689 soil Substances 0.000 claims abstract description 39
- 239000002699 waste material Substances 0.000 claims abstract description 10
- 239000000356 contaminant Substances 0.000 claims description 23
- 239000000725 suspension Substances 0.000 claims description 6
- 238000005507 spraying Methods 0.000 claims description 3
- 241000894006 Bacteria Species 0.000 abstract description 2
- 102000004190 Enzymes Human genes 0.000 description 5
- 108090000790 Enzymes Proteins 0.000 description 5
- 241000233866 Fungi Species 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 238000005086 pumping Methods 0.000 description 4
- 230000002195 synergetic effect Effects 0.000 description 4
- 235000001674 Agaricus brunnescens Nutrition 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- 239000002344 surface layer Substances 0.000 description 3
- 238000004056 waste incineration Methods 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
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- 101100325793 Arabidopsis thaliana BCA2 gene Proteins 0.000 description 1
- 241001494479 Pecora 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
- 150000002013 dioxins Chemical class 0.000 description 1
- 238000005553 drilling Methods 0.000 description 1
- 239000003337 fertilizer Substances 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
- 230000002209 hydrophobic effect Effects 0.000 description 1
- 239000007788 liquid Substances 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
Landscapes
- Processing Of Solid Wastes (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
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 contaminants which decomposes hardly decomposable substances contained in contaminated soil and adversely affecting the environment.
【0002】[0002]
【従来の技術】近年、廃棄物質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、土壌表面から約5〜30
cmの深さまでしか浸透しないことが分かった。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、土壌の表層部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, so that most of them do not penetrate deep into the soil, but only about 5 to 30
It was found to penetrate only to a depth of cm. 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】そこで、本発明は、汚染
土壌に対し、一又は複数の管を所定の深さまで挿入し、
この管を通じて菌床またはその粉砕物、あるいは懸濁液
状にした菌床を挿入することによる汚染物質処理方法を
提案する。また、本発明は、汚染土壌に対し、菌床の溶
解液または懸濁液を撒布または注入することによる汚染
物質処理方法を提案する。上記方法において、菌床は、
食用菌菌床または廃菌床であってもよい。SUMMARY OF THE INVENTION Accordingly, the present invention provides a method for inserting one or more tubes into a contaminated soil to a predetermined depth.
A method for treating contaminants by inserting a bacterial bed or a crushed product thereof or a bacterial bed in a suspension form through this tube is proposed. The present invention also proposes a method for treating contaminants by spraying or injecting a solution or suspension of a bacterial bed on contaminated soil. In the above method, the bacterial bed is
It may be an edible bacterial bed or a waste bacterial bed.
【0009】[0009]
【発明の実施の形態】《実施例1》まず、汚染物質分解
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、例えば図1に概略的に示す
ように、上記粉体菌床を収容するタンク1と、このタン
ク1から粉体菌床を圧送するための、圧送管2Aおよび
ポンプ2Bからなる圧送手段2と、この圧送手段2を介
して上記タンク1と連結され、走行可能な重機Mのアー
ムA先端に取り付けられた板状のヘッド3と、このヘッ
ド3から突設された複数の中空の管状突起部4とを備え
る装置5を用いて、汚染土壌に粉体菌床を注入して添加
する。具体的には、重機MのアームAを操作することに
よりヘッド3を土壌面に押し付けてヘッド面を土壌面に
当接させると、ヘッド3から突設された管状突起部4が
その突出長さ分だけ土壌に挿入される。この状態で、ポ
ンプ2Bを駆動すると、タンク1に収容された粉体菌床
が圧送管2Aを通じて管状突出部4から土壌中に注入さ
れることとなる。ここで、管状突起部4の長さを約5〜
30cm、好ましくは約15〜25cmに設定し、粉体
菌床を注入する深さを地表面から約5〜30cm、好ま
しく約15〜25cmとする。これは、多くの汚染物質
は疎水性が高く、土壌表面から約5〜30cmの深さま
でしか存在しないからである。BEST MODE FOR CARRYING OUT THE INVENTION Example 1 First, a bacterial bed (edible bacterial bed or waste bacterial bed) capable of decomposing contaminants is ground into a powder. For example, as schematically shown in FIG. 1, a tank 1 for accommodating the powdered bacterial bed and a pumping means 2 comprising a pumping pipe 2A and a pump 2B for pumping the powdered bacterial bed from the tank 1. And a plate-shaped head 3 connected to the tank 1 via the pumping means 2 and attached to the end of the arm A of the movable heavy machine M, and a plurality of hollow tubular projections protruding from the head 3 The powdered bacterial bed is injected and added to the contaminated soil by using the apparatus 5 including the section 4. Specifically, when the head 3 is pressed against the soil surface by operating the arm A of the heavy equipment M to bring the head surface into contact with the soil surface, the tubular projection 4 protruding from the head 3 has a protrusion length. Minutes are inserted into the soil. When the pump 2B is driven in this state, the powdered bacterial bed stored in the tank 1 is injected into the soil from the tubular protrusion 4 through the pressure pipe 2A. Here, the length of the tubular projection 4 is about 5 to
The depth is set at 30 cm, preferably about 15 to 25 cm, and the depth at which the powdered bacterial bed is injected is about 5 to 30 cm, preferably about 15 to 25 cm from the ground surface. This is because many contaminants are highly hydrophobic and only exist at a depth of about 5 to 30 cm from the soil surface.
【0010】数週間経過すると、廃棄物に混合した菌床
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、廃棄物中の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 bacterial bed mixed with the waste, and decomposing enzymes are generated during this growth process. The contaminants in the waste are decomposed and made harmless by the synergistic effect of the grown hypha 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】この実施例では、アームAを操作すること
により、管状突出部4を備えたヘッド3の角度を任意に
変更できるので、対象土壌が図1のように傾斜していて
も菌床を供給することができる。In this embodiment, by operating the arm A, the angle of the head 3 provided with the tubular protrusion 4 can be changed arbitrarily, so that even if the target soil is inclined as shown in FIG. Can be supplied.
【0012】《実施例2》まず、汚染物質分解能力のあ
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、図2に示すように、長さ約5〜30
cm、好ましくは約15〜25cmの複数の突起部6を
有するシープスフットローラ7を用い、廃棄物焼却場付
近の汚染物質を含む汚染土壌の表面に突起部6を挿入し
て深さ約5〜30cm、好ましくは約15〜25cmの
孔を穿孔した後、この孔に粉体状の菌床を挿入する。本
実施例においても、実施例1と同様に、菌床から成長し
た菌糸と分解酵素との相乗効果により、汚染土壌中の汚
染物質を分解処理することができる。Example 2 First, a bacterial bed (edible bacterial bed or waste bacterial bed) capable of decomposing contaminants is ground into a powder. Then, as shown in FIG.
cm, preferably about 15 to 25 cm, is inserted into the surface of contaminated soil containing contaminants near the waste incineration plant by using a sheep foot roller 7 having a plurality of protrusions 6 having a depth of about 5 cm. After drilling a hole of 〜30 cm, preferably about 15-25 cm, a powdery bacterial bed is inserted into this hole. In this embodiment, as in the first embodiment, the contaminants in the contaminated soil can be decomposed by the synergistic effect of the hypha and the decomposing enzyme grown from the bacterial bed.
【0013】《実施例3》汚染物質分解能力のある菌床
(食用菌菌床または廃菌床)を粉砕して粉体状にし、こ
れを水に溶かして懸濁液を作成しておく。そしてこの懸
濁液を、液体肥料を撒布するのに使用されるリッピング
チラーを用いて、廃棄物焼却場付近の汚染物質を含む汚
染土壌の表面上に撒布して土壌の表層部に浸透させる。
撒布後、必要に応じて、土壌表面をレーキのような手段
を用いて汚染土が周囲に飛散しないように均してもよ
い。本実施例においても、実施例1と同様に、菌床から
成長した菌糸と分解酵素との相乗効果により、汚染土壌
中の汚染物質を分解処理することができる。<< Example 3 >> A bacterial bed (edible bacterial bed or waste bacterial bed) capable of decomposing contaminants is pulverized into powder, which is dissolved in water to prepare a suspension. The suspension is then spread on the surface of contaminated soil containing contaminants near the waste incineration plant using a ripping chiller used to spray liquid fertilizer to penetrate the surface layer of the soil.
After the spraying, if necessary, the surface of the soil may be leveled by using means such as a rake so that the contaminated soil does not scatter around. In this embodiment, as in the first embodiment, the contaminants in the contaminated soil can be decomposed by the synergistic effect of the hypha and the decomposing enzyme grown from the bacterial bed.
【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
壌の表面から所定の深さまで注入、挿入または浸透させ
る本発明の構成によれば、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のできる。また、菌床を汚染
土壌の表層部だけに供給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 configuration of the present invention in which a bacterial bed having a capability of decomposing contaminants is injected, inserted or penetrated from the surface of the contaminated soil to a predetermined depth, it is not necessary to use a large-sized machine. The contaminants can be effectively decomposed without being scattered around. Further, since the bacterial bed is supplied only to 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例を示す概
略図である。FIG. 1 is a schematic view showing one embodiment of a method for treating contaminants of the present invention.
【図2】本発明の汚染物質処理方法の他の実施例を示す
概略図である。FIG. 2 is a schematic view showing another embodiment of the method for treating pollutants of the present invention.
【図3】本発明の汚染物質処理方法のさらに他の実施例
を示す概略図である。FIG. 3 is a schematic view showing still another embodiment of the method for treating contaminants of the present invention.
───────────────────────────────────────────────────── フロントページの続き (72)発明者 岡田 俊也 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 AA71X BB04 BC41 BC50 CA27 CA56 4D004 AA41 AB03 AB05 AB06 AB07 AC07 CA18 CA50 CC07 ────────────────────────────────────────────────── ─── Continued on the front page (72) Inventor Toshiya Okada 4-640 Shimoseito, Kiyose-shi, Tokyo F-term in Obayashi Corporation Technical Research Institute Co., Ltd. 4B065 AA71X BB04 BC41 BC50 CA27 CA56 4D004 AA41 AB03 AB05 AB06 AB07 AC07 CA18 CA50 CC07
Claims (3)
の深さまで挿入し、この管を通じて菌床またはその粉砕
物、あるいは菌床の溶解液または懸濁液を注入すること
を特徴とする汚染物質処理方法。1. A method comprising inserting one or more tubes into a contaminated soil to a predetermined depth, and injecting a bacterial bed or a crushed product thereof, or a solution or suspension of the bacterial bed through the tubes. Pollutant treatment method.
濁液を撒布または注入することによる汚染物質処理方
法。2. A method for treating contaminants by spraying or pouring a solution or suspension of a bacterial bed onto contaminated soil.
あることを特徴とする請求項1または2に記載の汚染物
質処理方法。3. 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 |
---|---|---|---|
JP2000201336A JP2002018424A (en) | 2000-07-03 | 2000-07-03 | Method for treating pollutant |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2000201336A JP2002018424A (en) | 2000-07-03 | 2000-07-03 | Method for treating pollutant |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2002018424A true JP2002018424A (en) | 2002-01-22 |
Family
ID=18699050
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2000201336A Pending JP2002018424A (en) | 2000-07-03 | 2000-07-03 | Method for treating pollutant |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2002018424A (en) |
-
2000
- 2000-07-03 JP JP2000201336A patent/JP2002018424A/en active Pending
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