Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JP5284255B2 - Purification method for contaminated soil - Google Patents
[go: Go Back, main page]

JP5284255B2 - Purification method for contaminated soil - Google Patents

Purification method for contaminated soil Download PDF

Info

Publication number
JP5284255B2
JP5284255B2 JP2009287822A JP2009287822A JP5284255B2 JP 5284255 B2 JP5284255 B2 JP 5284255B2 JP 2009287822 A JP2009287822 A JP 2009287822A JP 2009287822 A JP2009287822 A JP 2009287822A JP 5284255 B2 JP5284255 B2 JP 5284255B2
Authority
JP
Japan
Prior art keywords
electrode
contaminated soil
dioxins
discharge
terminal
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
JP2009287822A
Other languages
Japanese (ja)
Other versions
JP2011125808A (en
Inventor
成郎 北原
敏 内藤
定頼 保科
幸雄 垣内
守 平林
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.)
Kumagai Gumi Co Ltd
Fatec Co Ltd
Original Assignee
Kumagai Gumi Co Ltd
Fatec Co Ltd
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 Kumagai Gumi Co Ltd, Fatec Co Ltd filed Critical Kumagai Gumi Co Ltd
Priority to JP2009287822A priority Critical patent/JP5284255B2/en
Publication of JP2011125808A publication Critical patent/JP2011125808A/en
Application granted granted Critical
Publication of JP5284255B2 publication Critical patent/JP5284255B2/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

  • Processing Of Solid Wastes (AREA)

Description

本発明は、PCBやダイオキシン類で汚染された汚染土壌を現場にて浄化可能な汚染土壌の浄化方法に関する。   The present invention relates to a method for purifying contaminated soil that can purify contaminated soil contaminated with PCBs or dioxins on site.

PCB(ポリ塩化ビフェニル又はポリクロロビフェニル)やダイオキシン類(ポリ塩化ジベンゾパラジオキシン及びポリ塩化ジベンゾフラン)で汚染された汚染土壌を浄化する方法として、汚染土壌を加熱して浄化する加熱浄化装置を用いる方法が知られている(特許文献1など参照)。   As a method of purifying contaminated soil contaminated with PCB (polychlorinated biphenyl or polychlorinated biphenyl) or dioxins (polychlorinated dibenzopararadixin and polychlorinated dibenzofuran), a method using a heating and purifying apparatus that purifies the contaminated soil by heating. Is known (see Patent Document 1).

特開2008−062168号公報JP 2008-062168

しかしながら、上述した加熱浄化装置を用いた浄化方法では、汚染土壌を加熱浄化装置の設置場所まで運搬しなければならず、運搬中に汚染土壌が飛散したり、運搬コスト、処理コストがかかるなどの問題点があった。
本発明は、汚染土壌を汚染現場にて浄化でき、汚染土壌の飛散、運搬コスト、処理コストの問題を解消できる汚染土壌の浄化方法を提供する。
However, in the purification method using the heating purification device described above, the contaminated soil must be transported to the place where the heating purification device is installed, and the contaminated soil is scattered during transportation, which incurs transportation costs and processing costs. There was a problem.
The present invention provides a method for purifying contaminated soil, which can purify contaminated soil at a contaminated site, and can solve the problems of scattering, transportation cost and treatment cost of contaminated soil.

本発明に係る汚染土壌の浄化方法は、PCBやダイオキシン類で汚染された汚染土壌中の浄化対象部に圧力波発生装置の圧力波発生部を設置して圧力波を発生させた後、浄化対象部に酸又はアルカリを加えてから水を加え、その後、浄化対象部に酵素液を加えた。このようにすれば、圧力波によって汚染土壌中のPCBやダイオキシン類を覆っている珪藻の殻が破壊され、酸又はアルカリによって珪藻の殻が水ガラス状態となり、さらに、浄化対象部に水を加えることで、水ガラス状態の殻と水とが反応してNaとなって地中下方に移動し、PCBやダイオキシン類が元の位置に残る。その後、PCBやダイオキシン類が残った浄化対象部に酵素液を加えることで、酵素液の酵素がPCBやダイオキシン類を分解する。従って、本発明によれば、汚染土壌を汚染現場にて浄化でき、汚染土壌の飛散、運搬コスト、処理コストの問題を解消できる。 In the method for purifying contaminated soil according to the present invention, the pressure wave generating unit of the pressure wave generating device is installed in the purification target portion in the contaminated soil contaminated with PCB or dioxins to generate a pressure wave, and then the target to be purified. After adding acid or alkali to the part, water was added, and then the enzyme solution was added to the part to be purified. In this way, the diatom shell covering the PCB and dioxins in the contaminated soil is destroyed by the pressure wave, the diatom shell becomes a water glass state by acid or alkali, and water is added to the purification target part. As a result, the water glass shell and water react to form Na 2 S i O 3 and move downward in the ground, leaving PCBs and dioxins in their original positions. Thereafter, an enzyme solution is added to the portion to be purified where PCBs and dioxins remain, so that the enzyme in the enzyme solution decomposes the PCBs and dioxins. Therefore, according to the present invention, the contaminated soil can be purified at the contaminated site, and the problems of scattering of the contaminated soil, transportation cost, and processing cost can be solved.

汚染土壌の浄化方法の手順を示す図。The figure which shows the procedure of the purification method of contaminated soil. 汚染土壌の浄化方法による汚染土壌中の様子を示す図。The figure which shows the mode in the contaminated soil by the purification method of contaminated soil. 酵素液の取り出し方法を示す図。The figure which shows the taking-out method of an enzyme liquid. 放電装置を示す図。The figure which shows a discharge device.

図1;図2に基づいて汚染土壌の浄化方法を説明する。まず、図1(a)に示すように、PCBやダイオキシン類で汚染された汚染土壌100における浄化対象部101の汚染土壌100中に後述する放電装置1(圧力波発生装置)の放電電極部6(圧力波発生部)を設置し、放電電極部6で放電させる放電処理を行う(図1(a)参照)。この場合、一般的にPCBやダイオキシン類は地表から50cm程度の地中に滞留するので、放電電極部6を浄化対象部101の地表から50cm程度下の地中に設置することが好ましい。この放電により生じた圧力波によって、汚染土壌100中においてPCB100aやダイオキシン類100bを覆っている珪藻102の殻103(二酸化珪素(S))が壊れる(図2(a)参照)。次に、放電処理後の浄化対象部101に酸104又はアルカリ105を加える(図1(b)参照)。これにより、珪藻102の殻103が水ガラス状態となる(図2(b)参照)。酸104又はアルカリ105を加えた後の浄化対象部101にさらに水106を加える(図1(c)参照)。これにより、水ガラス状態の殻103と水106とが反応してNaとなって地中下方に移動し、PCB100aやダイオキシン類100bが元の位置に残る(図2(c)参照)。つまり、PCBやダイオキシン類は、水に溶けないので、珪藻の殻が除去された後のシルト粒子である化石状態の微小藻類有機質の脂質部に溶解して元の位置に残る。その後、PCBやダイオキシン類が残った浄化対象部101に酵素液107を加える(図1(d)参照)。この酵素液107中の酵素が浄化対象部101のPCBやダイオキシン類を破壊するので、汚染土壌100が浄化される(図2(d)参照)。 FIG. 1; A method for purifying contaminated soil will be described with reference to FIG. First, as shown in FIG. 1A, a discharge electrode unit 6 of a discharge device 1 (pressure wave generator) described later in a contaminated soil 100 of a purification target portion 101 in a contaminated soil 100 contaminated with PCBs or dioxins. (Pressure wave generating part) is installed, and a discharge treatment is performed to discharge at the discharge electrode part 6 (see FIG. 1A). In this case, since PCBs and dioxins generally stay in the ground about 50 cm from the ground surface, it is preferable to install the discharge electrode portion 6 in the ground about 50 cm below the ground surface of the purification target portion 101. Due to the pressure wave generated by this discharge, the shell 103 (silicon dioxide (S i O 2 )) of the diatom 102 covering the PCB 100a and the dioxins 100b in the contaminated soil 100 is broken (see FIG. 2A). Next, the acid 104 or the alkali 105 is added to the purification target part 101 after the discharge treatment (see FIG. 1B). Thereby, shell 103 of diatom 102 will be in a water glass state (refer to Drawing 2 (b)). Water 106 is further added to the purification target portion 101 after the addition of the acid 104 or the alkali 105 (see FIG. 1C). As a result, the shell 103 in the water glass state and the water 106 react to form Na 2 S i O 3 and move downward in the ground, and the PCB 100a and dioxins 100b remain in their original positions (FIG. 2 (c)). reference). That is, since PCBs and dioxins are not soluble in water, they are dissolved in the lipid part of the fossilized microalgae organic substance, which is a silt particle after the diatom shell is removed, and remains in the original position. Thereafter, the enzyme solution 107 is added to the purification target portion 101 where PCBs and dioxins remain (see FIG. 1D). Since the enzyme in the enzyme solution 107 destroys the PCB and dioxins of the purification target portion 101, the contaminated soil 100 is purified (see FIG. 2 (d)).

上記酵素液107は例えば以下のように作成した。培養した菌を遠心分離器で遠心分離し、沈殿した菌を集菌する。遠心分離器で遠心分離することで、濃厚な菌群を得ることができる。そして、得られた菌群中に電極装置の放電電極部を設置して放電し、放電による圧力波で菌110の細胞膜111を破壊することにより、細胞膜111で覆われていた酵素108を含む酵素液107を取り出すことができる(図3参照)。菌は、例えばコーンスティープリカー(コーンスターチの絞り糟)を水で40倍に薄めて中性にしたものに菌を接種し、70℃で8時間培養した菌を用いた。菌としては、PCBやダイオキシン類を破壊する酵素を有した菌であればよく、例えば、御堂筋菌(GeoBacillus
midousuji(アメリカンタイプカルチャーコレクション)ATCC 55926、ATCC 202050)、御堂筋菌の遺伝子を入れた遺伝子組み換え菌などを用いることができる。
The enzyme solution 107 was prepared as follows, for example. The cultured bacteria are centrifuged with a centrifuge, and the precipitated bacteria are collected. A dense fungus group can be obtained by centrifuging with a centrifuge. Then, a discharge electrode part of the electrode device is placed in the obtained fungus group and discharged, and the cell membrane 111 of the fungus 110 is destroyed by a pressure wave due to the discharge, thereby containing an enzyme 108 covered with the cell membrane 111. The liquid 107 can be taken out (see FIG. 3). As the fungus, for example, a fungus obtained by inoculating a corn steep liquor (corn starch squeezed rice cake) diluted 40-fold with water to neutrality and culturing at 70 ° C. for 8 hours was used. As the fungus, any fungus having an enzyme that destroys PCBs and dioxins may be used. For example, Midosuji (GeoBacillus)
midousuji (American Type Culture Collection) ATCC 55926, ATCC 202050), genetically modified bacteria containing a Midosuji gene, and the like can be used.

図4に示すように、放電装置1は、電極装置2と、電源装置3と、電極装置2と電源装置3とを電気的に接続するための接続体30とを備える。   As shown in FIG. 4, the discharge device 1 includes an electrode device 2, a power supply device 3, and a connection body 30 for electrically connecting the electrode device 2 and the power supply device 3.

電極装置2は、間隔維持手段6Aによって間隔(放電ギャップ)gを隔てて配置された正負の電極4;5からなる放電電極部6を備える。   The electrode device 2 includes a discharge electrode portion 6 composed of positive and negative electrodes 4; 5 arranged at an interval (discharge gap) g by an interval maintaining means 6A.

電極4;5は、電極構成体4A;5Aの一端により形成される。電極構成体4A;5Aは、例えば線径2mm〜3mm程度の銅線のような導体線の周囲がビニル樹脂などの樹脂で被覆された線径4mm〜5mm程度のいわゆる被覆線により形成され、この場合、電極4;5は、被覆線の一端において露出する導体線の一端により形成されることになる。一端が正の電極4となる電極構成体4Aの他端には正極端子4aが設けられ、一端が負の電極5となる電極構成体5Aの他端には負極端子5aが設けられる。   The electrode 4; 5 is formed by one end of the electrode assembly 4A; 5A. The electrode structure 4A; 5A is formed of a so-called coated wire having a wire diameter of about 4 mm to 5 mm, for example, in which a conductor wire such as a copper wire having a wire diameter of about 2 mm to 3 mm is coated with a resin such as vinyl resin. In this case, the electrodes 4; 5 are formed by one end of the conductor wire exposed at one end of the covered wire. A positive electrode terminal 4 a is provided at the other end of the electrode structure 4 </ b> A whose one end is the positive electrode 4, and a negative electrode terminal 5 a is provided at the other end of the electrode structure 5 </ b> A whose one end is the negative electrode 5.

直線状態の電極構成体4A;5Aの一端(電極4;5)側を直線状態から直角に折り曲げることにより、互いに直角関係なL字状の一端部を形成する。折り曲げられた部分4B;5B(以下、電極部という)の一端(電極4;5)同士が間隔gを隔てて配置され、間隔維持手段6Aによって当該間隔gが保持された正負の電極4;5からなる放電電極部6が形成される。間隔維持手段6Aは絶縁体により形成され、例えば、電極部4B;5Bにそれぞれ挟み付けられて取り付けられる挟着体6d;6dを両端に備え、互いに対向するように設けられた一対の挟着体6d;6d間の間隔bが間隔維持材6eにより維持された構成である。間隔維持手段6Aは、接着剤などで電極部4B;5Bに取り付けられて電極4;5が間隔gを隔てて対向するように電極部4B;5B同士を連結する図外の棒状絶縁体により構成してもよい。   By bending one end (electrode 4; 5) side of the electrode structure 4A; 5A in a straight line at a right angle from the straight state, L-shaped one end portions having a right angle relationship with each other are formed. One end (electrode 4; 5) of the bent portion 4B; 5B (hereinafter referred to as an electrode portion) is arranged with a gap g therebetween, and the positive and negative electrodes 4; 5 with the gap g held by the gap maintaining means 6A. A discharge electrode portion 6 made of is formed. The spacing maintaining means 6A is formed of an insulator, for example, a pair of sandwiching bodies provided at both ends with sandwiching bodies 6d; 6d that are sandwiched and attached to the electrode portions 4B; 6d; the interval b between 6d is maintained by the interval maintaining member 6e. The interval maintaining means 6A is composed of a rod-shaped insulator (not shown) that connects the electrode portions 4B; 5B to each other so that the electrodes 4; May be.

電源装置3は、昇圧装置12、パルスパワー出力装置13を備える。
昇圧装置12は、電源電圧入力部14A、図外の変圧器を備えた昇圧回路15、出力部14を備える。
昇圧回路15は、電源電圧入力部14Aに接続された電源ケーブル14C経由で例えば三相交流200V電源電圧を入力して例えば直流20kV〜50kVの電圧を生成し、生成した直流20kV〜50kVの電圧を出力部14より出力する。出力部14は、正極端子14aと負極端子14bとを備える。
The power supply device 3 includes a booster device 12 and a pulse power output device 13.
The booster 12 includes a power supply voltage input unit 14A, a booster circuit 15 including a transformer (not shown), and an output unit 14.
The booster circuit 15 inputs, for example, a three-phase AC 200V power supply voltage via a power cable 14C connected to the power supply voltage input unit 14A to generate a voltage of DC 20 kV to 50 kV, for example, and generates the generated voltage of DC 20 kV to 50 kV. Output from the output unit 14. The output unit 14 includes a positive terminal 14a and a negative terminal 14b.

パルスパワー出力装置13は、入力端子16、充電回路17、出力部としての電極接続部18を備える。入力端子16は、正極端子16aと負極端子16bとを備える。電極接続部18は、正極端子18aと負極端子18bとを備える。充電回路17は、正極線17a、負極線17b、コンデンサ20、スイッチ21;22を備える。正極線17aには、スイッチ21とスイッチ22とが直列に接続される。正極線17aの一端が入力端子16の正極端子16aに接続され、正極線17aの他端が電極接続部18の正極端子18aに接続される。負極線17bの一端が入力端子16の負極端子16bに接続され、負極線17bの他端が電極接続部18の負極端子18bに接続される。コンデンサ20は、正極線17aにおけるスイッチ21とスイッチ22との間の接続点と負極線17bとに接続される。即ち、コンデンサ20は、正極線17a及び負極線17bに並列接続される。スイッチ21は昇圧装置12から供給された電圧をコンデンサ20に充電させるためのスイッチ、スイッチ22はコンデンサ20に充電された電荷を放電させて電極接続部18経由で電極装置2に出力させるためのスイッチである。図示しないが、充電回路17は接地(アース)されている。   The pulse power output device 13 includes an input terminal 16, a charging circuit 17, and an electrode connection unit 18 as an output unit. The input terminal 16 includes a positive terminal 16a and a negative terminal 16b. The electrode connecting portion 18 includes a positive terminal 18a and a negative terminal 18b. The charging circuit 17 includes a positive electrode line 17a, a negative electrode line 17b, a capacitor 20, and switches 21; 22. A switch 21 and a switch 22 are connected in series to the positive electrode line 17a. One end of the positive electrode line 17 a is connected to the positive electrode terminal 16 a of the input terminal 16, and the other end of the positive electrode line 17 a is connected to the positive electrode terminal 18 a of the electrode connection part 18. One end of the negative electrode wire 17 b is connected to the negative electrode terminal 16 b of the input terminal 16, and the other end of the negative electrode wire 17 b is connected to the negative electrode terminal 18 b of the electrode connection portion 18. The capacitor 20 is connected to a connection point between the switch 21 and the switch 22 in the positive electrode line 17a and the negative electrode line 17b. That is, the capacitor 20 is connected in parallel to the positive electrode line 17a and the negative electrode line 17b. The switch 21 is a switch for charging the capacitor 20 with the voltage supplied from the booster 12, and the switch 22 is a switch for discharging the charge charged in the capacitor 20 and outputting it to the electrode device 2 via the electrode connection unit 18. It is. Although not shown, the charging circuit 17 is grounded.

接続体30は、接続ケーブル31と、接続ケーブル31の一端に設けられた入力側コネクタ32と、接続ケーブル31の他端に設けられた出力側コネクタ33とを備える。入力側コネクタ32は、電源装置3の電極接続部18の正極端子18a及び負極端子18bの各々に接続される正極端子32a及び負極端子32bを備える。出力側コネクタ33は、電極構成体4Aの正極端子4aに接続される正極端子33a及び電極構成体5Aの負極端子5aに接続される負極端子33bを備える。   The connection body 30 includes a connection cable 31, an input-side connector 32 provided at one end of the connection cable 31, and an output-side connector 33 provided at the other end of the connection cable 31. The input-side connector 32 includes a positive terminal 32 a and a negative terminal 32 b that are connected to each of the positive terminal 18 a and the negative terminal 18 b of the electrode connection portion 18 of the power supply device 3. The output side connector 33 includes a positive electrode terminal 33a connected to the positive electrode terminal 4a of the electrode structure 4A and a negative electrode terminal 33b connected to the negative electrode terminal 5a of the electrode structure 5A.

次に、放電装置1の使用方法について説明する。接続体30の入力側コネクタ32と電源装置3の電極接続部18とを電気的に接続するとともに、接続体30の出力側コネクタ33と電極構成体4A;5Aとを電気的に接続する。電源装置3のスイッチ21、スイッチ22をともに非導通の状態としておいて、電源ケーブル14Cを介して電源装置3を交流200V電源に電気的に接続することで、電源ケーブル14Cを経由して昇圧装置12に交流200V電源が供給され、交流200Vが昇圧回路15で例えば直流20kV〜50kVに昇圧される。そして、スイッチ21を導通すると、コンデンサ20に電荷が蓄積される。コンデンサ20に電荷が蓄積された後に、スイッチ22を導通する。これにより電極装置2の放電電極部6の電極4;5に電圧が印加されて電極4;5間で放電を生じる。   Next, a method for using the discharge device 1 will be described. While connecting the input side connector 32 of the connection body 30 and the electrode connection part 18 of the power supply device 3, the output side connector 33 of the connection body 30 and the electrode structure 4A; 5A are electrically connected. By setting both the switch 21 and the switch 22 of the power supply device 3 to the non-conductive state and electrically connecting the power supply device 3 to the AC 200V power supply via the power supply cable 14C, the booster device via the power supply cable 14C is provided. 12 is supplied with AC 200V power, and the AC 200V is boosted by the booster circuit 15 to, for example, DC 20 kV to 50 kV. When the switch 21 is turned on, charge is accumulated in the capacitor 20. After the electric charge is accumulated in the capacitor 20, the switch 22 is turned on. As a result, a voltage is applied to the electrodes 4; 5 of the discharge electrode portion 6 of the electrode device 2 to generate a discharge between the electrodes 4;

上記電極装置2の代わりに、図4に示す電極装置2Aを用いてもよい。当該電極装置2Aは、例えば、+電極のような一方電極としての棒状の内部導体73と、内部導体73の外周囲を被覆する筒状の絶縁体74と、絶縁体74の外周囲に設けられた−電極のような他方電極としての外部導体75とにより構成される。即ち、当該電極装置2Aは、内部導体73と絶縁体74と外部導体75とが同軸状に配置された構成の同軸電極である。外部導体75は、内部導体73の中心線に沿った方向に間隔を隔てて設けられた複数の浮遊電極76;76・・・を構成する。浮遊電極とは、電源側と電気的に絶縁された電極のことである。絶縁体74の先端74tより突出して露出する内部導体73の先端部73tとこの先端部73tに最も近い浮遊電極76の先端部76tとで放電を生じさせる先端側放電ギャップ77が形成され、互いに対向する浮遊電極76同士の端部76sと端部76sとで放電を生じさせる中間側放電ギャップ78が形成される。中間側放電ギャップ78は複数形成される。先端側放電ギャップ77、中間側放電ギャップ78が維持された内部導体73と複数の浮遊電極76とにより放電電極部6が形成される。   Instead of the electrode device 2, an electrode device 2A shown in FIG. 4 may be used. The electrode device 2 </ b> A is provided, for example, on a rod-shaped inner conductor 73 as one electrode such as a + electrode, a cylindrical insulator 74 that covers the outer periphery of the inner conductor 73, and an outer periphery of the insulator 74. It is constituted by an outer conductor 75 as the other electrode such as an electrode. That is, the electrode device 2A is a coaxial electrode having a configuration in which the inner conductor 73, the insulator 74, and the outer conductor 75 are arranged coaxially. The outer conductor 75 constitutes a plurality of floating electrodes 76; 76... Spaced apart in the direction along the center line of the inner conductor 73. The floating electrode is an electrode that is electrically insulated from the power supply side. A leading end side discharge gap 77 is formed between the leading end portion 73t of the internal conductor 73 protruding from the leading end 74t of the insulator 74 and exposed, and the leading end portion 76t of the floating electrode 76 closest to the leading end portion 73t. An intermediate discharge gap 78 that generates a discharge is formed between the end portions 76s and the end portions 76s of the floating electrodes 76 that perform the discharge. A plurality of intermediate discharge gaps 78 are formed. The discharge electrode portion 6 is formed by the inner conductor 73 in which the front end side discharge gap 77 and the intermediate side discharge gap 78 are maintained and the plurality of floating electrodes 76.

実施形態によれば、汚染土壌を汚染現場にて浄化でき、汚染土壌の飛散、運搬コスト、処理コストの問題を解消できる。   According to the embodiment, the contaminated soil can be purified at the contaminated site, and the problems of scattering of the contaminated soil, transportation cost, and processing cost can be solved.

尚、上記では放電装置を用いたが、圧力波を発生させる装置であれば超音波装置などの他の圧力波発生装置を用いてもかまわない。   Although the discharge device is used in the above, other pressure wave generators such as an ultrasonic device may be used as long as the device generates pressure waves.

1 放電装置(圧力波発生装置)、6 放電電極部(圧力波発生部)、
100 汚染土壌、101 浄化対象部、104 酸、105 アルカリ、106 水、107 酵素液。
1 discharge device (pressure wave generator), 6 discharge electrode part (pressure wave generator),
100 contaminated soil, 101 part to be purified, 104 acid, 105 alkali, 106 water, 107 enzyme solution.

Claims (1)

PCBやダイオキシン類で汚染された汚染土壌中の浄化対象部に圧力波発生装置の圧力波発生部を設置して圧力波を発生させてPCBやダイオキシン類を覆っている珪藻の殻を破壊した後、浄化対象部に酸又はアルカリを加えて破壊した珪藻の殻を水ガラス状態としてから水を加えて水ガラス状態の殻を水と反応させてNa として地中下方に移動させ、その後、浄化対象部に酵素液を加えてPCBやダイオキシン類を酵素で分解することを特徴とする汚染土壌の浄化方法。 The pressure wave generator of the pressure wave generator was installed in the target area of the contaminated soil contaminated with PCBs and dioxins to generate pressure waves and destroyed the diatom shells covering the PCBs and dioxins . After that, the diatom shell destroyed by adding acid or alkali to the part to be purified is made into a water glass state, then water is added to cause the water glass state shell to react with water and move down into the ground as Na 2 S i O 3 A method for purifying contaminated soil, comprising: adding an enzyme solution to the portion to be purified and then decomposing PCB or dioxins with the enzyme .
JP2009287822A 2009-12-18 2009-12-18 Purification method for contaminated soil Expired - Fee Related JP5284255B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2009287822A JP5284255B2 (en) 2009-12-18 2009-12-18 Purification method for contaminated soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2009287822A JP5284255B2 (en) 2009-12-18 2009-12-18 Purification method for contaminated soil

Publications (2)

Publication Number Publication Date
JP2011125808A JP2011125808A (en) 2011-06-30
JP5284255B2 true JP5284255B2 (en) 2013-09-11

Family

ID=44288993

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2009287822A Expired - Fee Related JP5284255B2 (en) 2009-12-18 2009-12-18 Purification method for contaminated soil

Country Status (1)

Country Link
JP (1) JP5284255B2 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2014048060A (en) * 2012-08-29 2014-03-17 Kumagai Gumi Co Ltd Decontamination method
JP2014046223A (en) * 2012-08-29 2014-03-17 Kumagai Gumi Co Ltd Decontamination method

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001300510A (en) * 2000-04-25 2001-10-30 Kubota Corp Biological treatment method for persistent organic matter
JP3703368B2 (en) * 2000-05-30 2005-10-05 株式会社クボタ Purification method for contaminated soil, slurry, etc.
EP1337327B1 (en) * 2000-09-13 2010-03-17 Commonwealth Scientific And Industrial Research Organisation Process for treating a solid-liquid mixture
JP2009511265A (en) * 2005-10-20 2009-03-19 コモンウェルス サイエンティフィック アンド インダストリアル リサーチ オーガニゼイション Method for processing a solid-liquid mixture
JP5761920B2 (en) * 2009-10-06 2015-08-12 高砂熱学工業株式会社 Method for purifying dioxin-contaminated soil and method for decomposing dioxins in the soil

Also Published As

Publication number Publication date
JP2011125808A (en) 2011-06-30

Similar Documents

Publication Publication Date Title
WO2010057026A3 (en) Rechargeable stimulation lead, system, and method
JP5284255B2 (en) Purification method for contaminated soil
WO2012058289A3 (en) Uterine electrical stimulation system and method
EP1380346A4 (en) ELECTROSTATIC PARTICLE SEPARATION METHOD, PARTICLE ELECTROSTATIC SEPARATION APPARATUS AND PROCESSING SYSTEM
JPS5910386A (en) Liquid treating device with charge injector
WO2009143171A3 (en) Implantable neurostimulation electrode interface
Joannes et al. Review paper on cell membrane electroporation of microalgae using electric field treatment method for microalgae lipid extraction
JP3974442B2 (en) Sterilization apparatus and sterilization method
WO2012173405A3 (en) Apparatus and method for improving skin using a ra-effect or ra plus-effect
IN2012DN01833A (en)
WO2004029210A3 (en) Resolution of aggrecan gene expression using specific and selective electrical and electromagnetic signals
WO2016178501A1 (en) Low-temperature underwater plasma generating device
CN105948372A (en) Industrial sewage treatment technique and system based on high-voltage nanosecond pulsed electric field technology
KR20200066943A (en) Cell stimulation apparatus, ultrasound and electric stimulation apparatus
DE69608958D1 (en) WANDERFELDSCHEIDER FOR SEPARATING PARTICLES
Wang et al. Controlled release of DNA from carbon-paste microelectrodes
US7008787B2 (en) Chamber for the treating cells contained in a suspension in an electric field
CN1995361A (en) Method for promoting electroporation efficiency utilizing dielectrophoresis for assisting cell positioning
JP2014048060A (en) Decontamination method
NO874771L (en) PROCEDURE AND DEVICE FOR AA SUPPLY WITH CRUSHED ELECTRIC WIRES.
KR101838381B1 (en) Device for generating hydrogen water
CN102665453B (en) For the reactor assembly of electroporation
JP2014046223A (en) Decontamination method
GB2637628A (en) Methods and systems for transdermally stimulating a muscle
CN102780161A (en) Ion generator

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20121010

A711 Notification of change in applicant

Free format text: JAPANESE INTERMEDIATE CODE: A711

Effective date: 20121108

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20130314

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20130319

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20130513

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20130528

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20130529

R150 Certificate of patent or registration of utility model

Ref document number: 5284255

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

LAPS Cancellation because of no payment of annual fees