JP2013096983A - Method for decontaminating soil and soil decontaminating agent - Google Patents
Method for decontaminating soil and soil decontaminating agent Download PDFInfo
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- JP2013096983A JP2013096983A JP2011253235A JP2011253235A JP2013096983A JP 2013096983 A JP2013096983 A JP 2013096983A JP 2011253235 A JP2011253235 A JP 2011253235A JP 2011253235 A JP2011253235 A JP 2011253235A JP 2013096983 A JP2013096983 A JP 2013096983A
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本発明は、土壌除染方法および土壌除染剤に係り、特に、放射性物質が表層に付着した土壌の除染技術に関する。The present invention relates to a soil decontamination method and a soil decontamination agent, and more particularly, to a decontamination technique for soil in which a radioactive substance adheres to a surface layer.
原子力発電、原子力研究などの原子力関連施設や、放射性廃棄物の処理施設では、放射性物質の取扱い作業などによって、周辺の土壌がヨウ素,ストロンチウム,セシウム,プルトニウムなどの放射性物質によって汚染されることがある。また、それら施設が自然災害などの被害を受けて制御不能となり、放射性物質が大気中に放出される事故が発生すると、広範囲にわたる領域に放射性物質が堆積し、土壌が汚染されることもある。In nuclear power facilities such as nuclear power generation and nuclear power research and radioactive waste treatment facilities, the surrounding soil may be contaminated with radioactive materials such as iodine, strontium, cesium, and plutonium due to the handling of radioactive materials. . In addition, when these facilities become uncontrollable due to damage such as natural disasters, and an accident occurs in which radioactive materials are released into the atmosphere, radioactive materials may accumulate in a wide area and soil may be contaminated.
放射性物質には半減期の長い元素も多く、土壌表層に堆積したものは長期にわたって強い放射線を出し続けるので、周辺に生活する人にとっては放射線被曝による健康被害の危険性が高い。したがって、放射性物質の堆積した土壌については、なるべく早期の除染が望まれている。Many radioactive substances have long half-lives, and those deposited on the soil surface continue to emit strong radiation over a long period of time, so there is a high risk of health damage due to radiation exposure for those living in the vicinity. Therefore, decontamination as early as possible is desired for soil on which radioactive materials are deposited.
従来、放射性物質などの汚染物質が土壌に堆積した場合、ショベルカーなどの建設機械によって表土を掘り起こして回収し、最終処分場に運んで処理する除染方法が取られている。しかし、放射性物質によって汚染されているのは地表からわずかな深さであるのに対し、ショベルカーなどではかなり深く表土を掘り返し、回収することとなるので、処分する土砂の量が必要以上に多くなってしまう問題があった。除染する面積が大きいほど、回収した土砂の運搬や処分にも、膨大なコストがかかることになる。
さらに掘削、回収、運搬の各作業時には、土埃とともに汚染物質を含む粉塵が飛散し、周囲の環境に影響を与える2次汚染の可能性が高まるという課題もある。Conventionally, when pollutants such as radioactive substances accumulate on the soil, a decontamination method has been used in which the topsoil is dug and collected by a construction machine such as a shovel car and transported to a final disposal site. However, it is only a small depth from the surface that is contaminated by radioactive materials, but excavators and other equipment dig up and recover the top soil considerably, so the amount of soil to be disposed of is more than necessary. There was a problem that would become. The larger the area to be decontaminated, the greater the cost of transporting and disposing of the collected earth and sand.
In addition, during each excavation, collection, and transportation work, there is a problem that dust containing contaminants is scattered together with dust, and the possibility of secondary contamination that affects the surrounding environment is increased.
近年、このような課題に対して、下記の処理方法が提案されている。In recent years, the following processing methods have been proposed for such problems.
特許文献1は、粘着剤をポリマーシートの片面に張り付けてなる養生シートを有することを特徴とする除染シートである。また、特許文献2は、界面活性除染剤と光触媒からなるゲル除染剤を光触媒反応させて被汚染面に塗装被膜を形成し、皮膜を除去することにより除染することを特徴としている。さらに、特許文献3は、スチレン−ブタジエン共重合体などからなる水溶性エマルジョンを被除染面に塗布し、フィルム状にして除染することを特徴としている。 Patent Document 1 is a decontamination sheet having a curing sheet in which an adhesive is attached to one side of a polymer sheet. Further, Patent Document 2 is characterized in that a gel decontamination agent composed of a surface active decontamination agent and a photocatalyst is photocatalyzed to form a coating film on the contaminated surface and decontamination is performed by removing the film. Further, Patent Document 3 is characterized in that a water-soluble emulsion made of a styrene-butadiene copolymer or the like is applied to a surface to be decontaminated and is decontaminated into a film.
しかし、特許文献1のような除染方法では、粘着剤の表面積以上には汚染物質を取り込むことができず、しかも凹凸のある土壌表層面では充分に除染することができない。また、特許文献2のような除染方法および除染剤では、光触媒のコストが高い上に、ゲル化のためには紫外線、X線などの放射光発生装置が必要で、広範囲の土壌に適用することは困難である。さらに特許文献3のようなスチレン−ブタジエン共重合体などを含む除染剤は生物分解され難く、固化した表土の処分が困難な上、除染作業時に取り残しがあると、除染剤自体が土壌中に残留して、環境に負荷をかけるという課題があった。 However, in the decontamination method as in Patent Document 1, the contaminant cannot be taken in more than the surface area of the pressure-sensitive adhesive, and furthermore, it cannot be sufficiently decontaminated on the uneven soil surface. In addition, the decontamination method and decontamination agent as disclosed in Patent Document 2 are expensive in photocatalysts, and need a radiation generator such as ultraviolet rays and X-rays for gelation, and can be applied to a wide range of soils. It is difficult to do. Furthermore, a decontamination agent containing a styrene-butadiene copolymer or the like as in Patent Document 3 is difficult to biodegrade, and it is difficult to dispose of the solid topsoil. There was a problem of remaining inside and putting a burden on the environment.
本発明者は、上記課題を解決すべく鋭意研究した結果、放射性物質に汚染された土壌表層面を除染するために、アルギン酸塩からなるゲルにより被汚染土壌表層面を吸着内包させ、除去することが有効であることを知見し、本発明に至った。 As a result of diligent research to solve the above-mentioned problems, the present inventor adsorbs and removes the contaminated soil surface with a gel made of alginate in order to decontaminate the soil surface contaminated with radioactive substances. Has been found to be effective, leading to the present invention.
すなわち、
(1) アルギン酸の一価金属塩と、アルギン酸塩以外の多価金属塩とを主な成分とする除染剤を、被除染土壌表層面に塗布または散布し、形成されるアルギン酸ゲルによって土壌表層を固化する工程と、固化した被除染土壌表層を地面から剥離除去する除去工程とを有することを特徴とする除染方法に関する。That is,
(1) A decontaminant mainly composed of a monovalent metal salt of alginic acid and a polyvalent metal salt other than alginates is applied or sprayed on the surface of the soil to be decontaminated, and the soil is formed by the alginate gel formed. The present invention relates to a decontamination method comprising a step of solidifying a surface layer and a removal step of peeling and removing the solidified decontaminated soil surface layer from the ground.
(2) また、請求項1記載の固化工程において、アルギン酸の一価金属塩を主な成分とする除染剤(A)と、アルギン酸塩以外の多価金属塩を主な成分とする除染剤(B)とに分け、被除染土壌表層面に対してA,Bを連続して散布または塗布し、ゲル化させることを特徴とする請求項1記載の除染方法に関する。(2) Further, in the solidifying step according to claim 1, a decontamination agent (A) mainly composed of a monovalent metal salt of alginic acid and a decontamination mainly composed of a polyvalent metal salt other than alginates. 2. The decontamination method according to claim 1, wherein the decontamination method is divided into the agent (B), and A or B is continuously sprayed or applied to the surface of the surface of the soil to be decontaminated for gelation.
(3) また、(1)〜(2)記載の除染剤であって、アルギン酸の一価金属塩が、アルギン酸ナトリウム、アルギン酸カリウム、またはアルギン酸アンモニウムの少なくとも1つであることを特徴とする(1)〜(2)のいずれか1項に記載の除染剤に関する。(3) The decontamination agent according to (1) to (2), wherein the monovalent metal salt of alginic acid is at least one of sodium alginate, potassium alginate, or ammonium alginate ( It is related with the decontamination agent of any one of 1)-(2).
(4) また、(1)〜(3)記載の除染剤であって、アルギン酸塩以外の多価金属塩が、カルシウム、亜鉛、銅、バリウム、鉄、アルミニウム、ニッケル及びマンガンからなる化合物の少なくとも1つであることを特徴とする、上記(1)〜(3)のいずれか1項に記載の除染剤に関する。(4) Moreover, it is a decontamination agent as described in (1)-(3), Comprising: The polyvalent metal salt other than an alginate is a compound which consists of calcium, zinc, copper, barium, iron, aluminum, nickel, and manganese. It is related with the decontamination agent of any one of said (1)-(3) characterized by being at least one.
本発明は、イオン交換反応によってゲル化するアルギン酸の性質を応用した除染剤を塗布または散布するもので、広範囲かつ凹凸のある地表面であってもそれをまんべんなく覆い、表土をゲル化させて除去することができる。また、この除染剤は特殊な装置や硬化剤を使うことなく、常温でゲル化して固化するので、除染処理が容易でかつ除染にかかるコストを低減することができる。また、土壌表層部の汚染層だけを集中的に固化し、剥離除去することができるので、回収する汚染土壌の量を必要最小限に止めることができ、回収と処分にかかるコストを抑えられる上、処理すべき回収表土の集積場を小型化することもできる。また、回収する表土はゲル化され、フィルム状に固化しているため、除染作業時、運搬時などにおいて粉塵が発生せず、作業者が放射性物質を吸引したり、周辺に飛散したりするのを防ぐことができる。さらに、本発明による除染剤は主成分が天然植物由来のアルギン酸であることから、処理後の残留物は容易に生物分解され、環境への負担が少ない。 The present invention applies or spreads a decontamination agent applying the properties of alginic acid that gels by an ion exchange reaction. Even if it covers a wide and uneven ground surface, it covers evenly and gels the topsoil. Can be removed. Further, since this decontaminating agent gels and solidifies at room temperature without using a special device or curing agent, the decontamination treatment is easy and the cost for decontamination can be reduced. In addition, since only the contaminated layer on the surface layer of the soil can be solidified and separated and removed, the amount of contaminated soil to be collected can be kept to a minimum and the costs for recovery and disposal can be reduced. It is also possible to reduce the size of the collection ground for the recovered topsoil to be processed. In addition, since the topsoil to be collected is gelled and solidified into a film, dust is not generated during decontamination work, transportation, etc., and the operator sucks radioactive materials or scatters around Can be prevented. Furthermore, since the main component of the decontamination agent according to the present invention is alginic acid derived from a natural plant, the residue after treatment is easily biodegraded, and the burden on the environment is small.
以下、実施例により本発明を具体的に説明するが、本発明はこれらに限定されるものではない。 EXAMPLES Hereinafter, the present invention will be specifically described with reference to examples, but the present invention is not limited thereto.
第一実施例として、
アルギン酸ナトリウム水溶液からなる除染剤(A)と、塩化カルシウム水溶液からなる除染剤(B)を用意する。As a first example,
A decontamination agent (A) composed of an aqueous sodium alginate solution and a decontamination agent (B) composed of an aqueous calcium chloride solution are prepared.
次に、除染剤(A)を任意の手段、例えばブラシまたはローラー、シャワーあるいは噴霧によって被汚染土壌表層面に塗布または散布する。続いて除染剤(B)を任意の手段、例えばブラシ、ローラー、シャワーあるいは噴霧によって、図1のように被除染土壌表層面に塗布する。この時、除染剤(A)と除染剤(B)を塗布する順序および回数に特に制限は無い。 Next, the decontaminating agent (A) is applied to or spread on the surface of the contaminated soil by any means such as a brush or roller, shower or spray. Subsequently, the decontamination agent (B) is applied to the surface of the soil to be decontaminated as shown in FIG. 1 by any means such as a brush, roller, shower or spray. At this time, there is no restriction | limiting in particular in the order and frequency | count of apply | coating a decontaminating agent (A) and a decontaminating agent (B).
除染剤(A)と除染剤(B)が接触混合することにより、除染剤中のアルギン酸分子とカルシウムイオンによるイオン架橋反応が起こりゲル化する。この際、図2のように、除染剤が土壌表層をゲル中に包含するので、放射性物質等の汚染物質も土壌と共に固化する。 By contacting and mixing the decontaminating agent (A) and the decontaminating agent (B), an ionic crosslinking reaction is caused by alginic acid molecules and calcium ions in the decontaminating agent, and gelation occurs. At this time, as shown in FIG. 2, since the decontamination agent includes the soil surface layer in the gel, contaminants such as radioactive substances are solidified together with the soil.
所定の時間が経過し十分にゲル化が進行すると、図3に示すようにゲル化した除染剤と共に固化した表土を地面から剥離、除去することができるようになる。 When the gelation proceeds sufficiently after a predetermined time has elapsed, as shown in FIG. 3, the topsoil solidified with the gelled decontamination agent can be peeled off and removed from the ground.
第二実施例として、
アルギン酸ナトリウムと硫酸カルシウム、およびゲル化時間調整剤としてピロリン酸ナトリウム、グルコノデルタラクトンを含む除染剤(C)を用意し、これを溶解して水溶液とする。As a second example,
A decontamination agent (C) containing sodium alginate and calcium sulfate and sodium pyrophosphate and glucono delta lactone as a gelation time adjusting agent is prepared and dissolved to obtain an aqueous solution.
除染剤(C)の溶液を任意の手段、例えばブラシ、ローラー、シャワーあるいは噴霧によって、被除染土壌表面に塗布または散布する。 The solution of the decontaminating agent (C) is applied or spread on the surface of the soil to be decontaminated by any means such as a brush, roller, shower or spray.
除染剤(C)に含まれるアルギン酸ナトリウムとカルシウム塩は、ゲル化時間調整剤の働きにより、表土に浸透した後にイオン化し、架橋反応によりゲル化する。この際、図2のように除染剤が土壌表層をゲル中に包含するので、放射性物質等の汚染物質は土壌と共に固化する。 The sodium alginate and calcium salt contained in the decontamination agent (C) are ionized after penetrating into the top soil by the action of the gelation time adjusting agent and gelled by a crosslinking reaction. At this time, as shown in FIG. 2, the decontamination agent includes the soil surface layer in the gel, so that contaminants such as radioactive substances are solidified together with the soil.
所定の時間が経過し十分にゲル化が進行すると、図3に示すようにゲル化した除染剤と共に固化した表土を地面から剥離、除去することができるようになる。 When the gelation proceeds sufficiently after a predetermined time has elapsed, as shown in FIG. 3, the topsoil solidified with the gelled decontamination agent can be peeled off and removed from the ground.
本実施例においては、いずれの実施例においても土壌表層を表面から5mm程度剥離することができた。非特許文献(第34回原子力委員会資料第1号 2011年 15頁)によると、放射性物質汚染土壌の表層から5mmを除去すると、線量率が3分の1に下がるという結果が示されており、本実施例は十分な除染効果があることが推察される。 In this example, the soil surface layer could be peeled from the surface by about 5 mm in any of the examples. According to non-patent literature (34th Atomic Energy Commission document No. 1, 2011, page 15), the removal of 5mm from the surface layer of radioactive material contaminated soil shows that the dose rate drops to one third. This example is presumed to have a sufficient decontamination effect.
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JP2019015658A (en) * | 2017-07-10 | 2019-01-31 | 太平電業株式会社 | Method for processing used decontamination agent |
CN111135800A (en) * | 2020-01-10 | 2020-05-12 | 景德镇一牧堂陶瓷科技有限公司 | Biochar material for efficiently reducing arsenic pollution of soil and preparation method thereof |
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JP2019015658A (en) * | 2017-07-10 | 2019-01-31 | 太平電業株式会社 | Method for processing used decontamination agent |
CN111135800A (en) * | 2020-01-10 | 2020-05-12 | 景德镇一牧堂陶瓷科技有限公司 | Biochar material for efficiently reducing arsenic pollution of soil and preparation method thereof |
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