JP6010286B2 - Purification method of radioactively contaminated soil - Google Patents
Purification method of radioactively contaminated soil Download PDFInfo
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- JP6010286B2 JP6010286B2 JP2011189240A JP2011189240A JP6010286B2 JP 6010286 B2 JP6010286 B2 JP 6010286B2 JP 2011189240 A JP2011189240 A JP 2011189240A JP 2011189240 A JP2011189240 A JP 2011189240A JP 6010286 B2 JP6010286 B2 JP 6010286B2
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- 239000002689 soil Substances 0.000 title claims description 102
- 238000000034 method Methods 0.000 title claims description 18
- 238000000746 purification Methods 0.000 title claims description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 39
- 239000003795 chemical substances by application Substances 0.000 claims description 15
- 239000010419 fine particle Substances 0.000 claims description 13
- 238000003756 stirring Methods 0.000 claims description 13
- 239000002245 particle Substances 0.000 claims description 12
- 239000000725 suspension Substances 0.000 claims description 7
- 230000002285 radioactive effect Effects 0.000 claims description 6
- 239000011362 coarse particle Substances 0.000 claims description 5
- 239000002270 dispersing agent Substances 0.000 description 15
- 239000003513 alkali Substances 0.000 description 7
- 238000011282 treatment Methods 0.000 description 7
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- 239000000941 radioactive substance Substances 0.000 description 5
- 239000007864 aqueous solution Substances 0.000 description 4
- 229910052792 caesium Inorganic materials 0.000 description 4
- TVFDJXOCXUVLDH-UHFFFAOYSA-N caesium atom Chemical compound [Cs] TVFDJXOCXUVLDH-UHFFFAOYSA-N 0.000 description 4
- 229910001385 heavy metal Inorganic materials 0.000 description 4
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 239000012857 radioactive material Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 2
- UIIMBOGNXHQVGW-UHFFFAOYSA-M Sodium bicarbonate Chemical compound [Na+].OC([O-])=O UIIMBOGNXHQVGW-UHFFFAOYSA-M 0.000 description 2
- 239000003337 fertilizer Substances 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- -1 salt compound Chemical class 0.000 description 2
- 235000011121 sodium hydroxide Nutrition 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- PNDPGZBMCMUPRI-HVTJNCQCSA-N 10043-66-0 Chemical compound [131I][131I] PNDPGZBMCMUPRI-HVTJNCQCSA-N 0.000 description 1
- KXDHJXZQYSOELW-UHFFFAOYSA-N Carbamic acid Chemical class NC(O)=O KXDHJXZQYSOELW-UHFFFAOYSA-N 0.000 description 1
- 229910052778 Plutonium Inorganic materials 0.000 description 1
- CIOAGBVUUVVLOB-NJFSPNSNSA-N Strontium-90 Chemical compound [90Sr] CIOAGBVUUVVLOB-NJFSPNSNSA-N 0.000 description 1
- 229910052770 Uranium Inorganic materials 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 235000011116 calcium hydroxide Nutrition 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 239000000292 calcium oxide Substances 0.000 description 1
- 235000012255 calcium oxide Nutrition 0.000 description 1
- 159000000007 calcium salts Chemical class 0.000 description 1
- TVFDJXOCXUVLDH-OUBTZVSYSA-N cesium-134 Chemical compound [134Cs] TVFDJXOCXUVLDH-OUBTZVSYSA-N 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 229910052732 germanium Inorganic materials 0.000 description 1
- GNPVGFCGXDBREM-UHFFFAOYSA-N germanium atom Chemical compound [Ge] GNPVGFCGXDBREM-UHFFFAOYSA-N 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 230000007062 hydrolysis Effects 0.000 description 1
- 238000006460 hydrolysis reaction Methods 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 229910000000 metal hydroxide Inorganic materials 0.000 description 1
- 150000004692 metal hydroxides Chemical class 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 150000007522 mineralic acids Chemical class 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 235000005985 organic acids Nutrition 0.000 description 1
- OYEHPCDNVJXUIW-UHFFFAOYSA-N plutonium atom Chemical compound [Pu] OYEHPCDNVJXUIW-UHFFFAOYSA-N 0.000 description 1
- 235000011118 potassium hydroxide Nutrition 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000004065 semiconductor Substances 0.000 description 1
- 235000017557 sodium bicarbonate Nutrition 0.000 description 1
- 229910000030 sodium bicarbonate Inorganic materials 0.000 description 1
- FQENQNTWSFEDLI-UHFFFAOYSA-J sodium diphosphate Chemical compound [Na+].[Na+].[Na+].[Na+].[O-]P([O-])(=O)OP([O-])([O-])=O FQENQNTWSFEDLI-UHFFFAOYSA-J 0.000 description 1
- 229940048086 sodium pyrophosphate Drugs 0.000 description 1
- 235000019832 sodium triphosphate Nutrition 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 239000010935 stainless steel Substances 0.000 description 1
- 235000019818 tetrasodium diphosphate Nutrition 0.000 description 1
- 239000001577 tetrasodium phosphonato phosphate Substances 0.000 description 1
- DNYWZCXLKNTFFI-UHFFFAOYSA-N uranium Chemical compound [U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U] DNYWZCXLKNTFFI-UHFFFAOYSA-N 0.000 description 1
- 238000011179 visual inspection Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
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Description
本発明は、放射能汚染土壌を、効率良く浄化する方法に関する。 The present invention relates to a method for efficiently purifying radioactively contaminated soil.
福島原子力発電所における放射性物質流出事故に伴い、農用地の放射性セシウムが国の暫定基準値（５０００Bq／kg）を超過した地域が広範囲に及ぶことが懸念され、汚染地の修復が喫緊の課題となっている。 Due to the radioactive material spill accident at the Fukushima nuclear power plant, there is a concern that the area where the radioactive cesium of agricultural land exceeded the national provisional standard value (5000 Bq / kg) will be widespread, and the restoration of contaminated areas has become an urgent issue. ing.
従来、重金属や放射性物質で汚染された土壌の浄化について検討され、例えば、重金属汚染土壌の浄化には、種々の薬剤を用いて、重金属含有土壌から重金属を溶出させて除去することにより、汚染土壌を浄化する方法が検討されている。例えば、薬剤として、カルシウム塩、有機酸、無機酸及びアミノカルボン酸から選ばれる１種以上の水溶液を用いて洗浄する方法（特許文献１）や、土壌ｐＨ（Ｈ2Ｏ）以下において加水分解により水酸イオンを配位して金属水酸化物を生成する金属塩化合物を用いて洗浄する方法（特許文献２）などが提案されている。
しかしながら、放射性物質汚染土壌について適用された例は知られていない。
Conventionally, purification of soil contaminated with heavy metals and radioactive materials has been studied. For example, for the purification of soil contaminated with heavy metals, various metals are used to elute and remove heavy metals from soil containing heavy metals. A method to purify is being studied. For example, as a chemical, a method of washing with one or more aqueous solutions selected from calcium salts, organic acids, inorganic acids, and aminocarboxylic acids (Patent Document 1), or hydrolysis under a soil pH (H 2 O) or lower. A method of washing with a metal salt compound that coordinates a hydroxide ion to produce a metal hydroxide (Patent Document 2) has been proposed.
However, there are no known examples applied to radioactive material contaminated soil.
従って、本発明の目的は、放射能汚染土壌を、効率良く浄化する方法を提供することにある。 Accordingly, an object of the present invention is to provide a method for efficiently purifying radioactively contaminated soil.
本発明者らは、斯かる実情に鑑み、種々検討した結果、放射能汚染土壌に水を導入し、土壌表面と水を攪拌した後、粗粒子画分を沈降させ、細粒子画分を含む土壌懸濁液を排水することにより、放射能汚染土壌を、効率良く浄化できることを見出し、本発明を完成した。 As a result of various studies in view of such circumstances, the present inventors have introduced water into radioactively contaminated soil, stirred the soil surface and water, and then settled the coarse particle fraction and included the fine particle fraction. The present inventors have found that the radioactively contaminated soil can be efficiently purified by draining the soil suspension, thereby completing the present invention.
すなわち、本発明は、放射能汚染土壌に、土壌表面からの水深が少なくとも５cmとなるように水を導入し、当該水と土壌表面を攪拌した後、放置し、土壌を粒径別に分級して粗粒子画分を沈降させた後、細粒子画分を除去することを特徴とする放射能汚染土壌の浄化方法を提供するものである。 That is, the present invention introduces water into radioactively contaminated soil so that the water depth from the soil surface is at least 5 cm, stirs the water and the soil surface, and then leaves the soil classified according to particle size. The present invention provides a method for purifying radioactively contaminated soil, wherein the coarse particle fraction is settled and then the fine particle fraction is removed.
本発明によれば、放射能汚染土壌を、効率良く浄化することができる。また、土壌表面のみを攪拌するため、作土全体に対する最終的な土壌損失量が少なく、浄化処理に伴う土壌排出量を抑制することができる。 According to the present invention, radioactively contaminated soil can be purified efficiently. Moreover, since only the soil surface is stirred, the final soil loss amount with respect to the whole soil is small, and the soil discharge amount accompanying a purification process can be suppressed.
本発明で浄化対象となる汚染土壌としては、市街地、山林、工業跡地、農用地（畑、水田）、沼地、排土等で、放射性物質を含有する土壌が挙げられる。
放射性物質としては、ヨウ素１３１、放射性セシウム（セシウム１３４、１３７）、ストロンチウム９０、ウラン、プルトニウム等が挙げられる。
特に、放射性セシウム汚染水田土壌の浄化に好適であり、現位置で浄化することができる。
Examples of the contaminated soil to be purified in the present invention include urban areas, mountain forests, industrial sites, agricultural land (fields, paddy fields), marshes, waste soil, and the like, which contain radioactive substances.
Examples of the radioactive substance include iodine 131, radioactive cesium (cesium 134, 137), strontium 90, uranium, and plutonium.
In particular, it is suitable for purification of radioactive cesium-contaminated paddy soil, and can be purified at the current position.
放射性物質、特に放射性セシウムは、土壌の最表面（０−２cm程度）に集積している。そこで、汚染土壌の表面のみを処理することにより、効率良く土壌を浄化することができる。
本発明においては、まず、土壌表面からの水深が５cm以上、好ましくは５〜２０cm、より好ましくは１０〜２０cmとなるように水を導入する。このような深さに水を導入することにより、土壌粒子が分散できる水厚を確保して粒径別に分級する効率を向上させ、排水中に土壌細粒子を多く含ませることができる。
水を水田土壌に導入する際には、畦畔に、水深より深い波板を設置するのが好ましい。
Radioactive substances, particularly radioactive cesium, are accumulated on the outermost surface of soil (about 0-2 cm). Therefore, the soil can be efficiently purified by treating only the surface of the contaminated soil.
In the present invention, first, water is introduced so that the water depth from the soil surface is 5 cm or more, preferably 5 to 20 cm, more preferably 10 to 20 cm. By introducing water at such a depth, it is possible to secure a water thickness at which soil particles can be dispersed and improve the efficiency of classification according to particle size, and to contain a large amount of soil fine particles in the drainage.
When water is introduced into paddy soil, it is preferable to install a corrugated sheet deeper than the water depth on the shore.
土壌表面に導入する水は、アルカリ剤又は分散剤を含有していても良い。
アルカリ剤としては、例えば、水酸化ナトリウム、水酸化カリウム、消石灰、生石灰、炭酸水素ナトリウム等が挙げられ；分散剤としては、ヘキサメタリン酸、ピロリン酸ナトリウム、トリポリリン酸ナトリウム等の化学的分散剤が挙げられる。
水田の土壌表面をアルカリ剤で処理する場合には、ｐＨ６〜１０、特に、ｐＨ８〜１０となるように用いるのが好ましい。このｐＨとするために、アルカリ剤の添加量は、１平米あたり０．１〜２モル量を用いるのが、土壌粒子を分散させる点から好ましい。
また、分散剤の濃度は０．１ｇ／Ｌ〜２ｇ／Ｌとするのが好ましい。
The water introduced into the soil surface may contain an alkali agent or a dispersant.
Examples of the alkaline agent include sodium hydroxide, potassium hydroxide, slaked lime, quicklime, sodium hydrogen carbonate and the like; examples of the dispersant include chemical dispersants such as hexametaphosphoric acid, sodium pyrophosphate and sodium tripolyphosphate. It is done.
When the soil surface of paddy fields is treated with an alkaline agent, it is preferably used so as to have a pH of 6 to 10, particularly 8 to 10. In order to obtain this pH, it is preferable to use an alkali agent in an amount of 0.1 to 2 mol per square meter from the viewpoint of dispersing soil particles.
The concentration of the dispersant is preferably 0.1 g / L to 2 g / L.
アルカリ剤又は分散剤は、水に溶解して水溶液として用いる以外に、土壌にアルカリ剤又は分散剤と水を別々に加えて混合しても良いし、水を含む土壌にアルカリ剤又は分散剤を混合しても良い。何れの場合にも、アルカリ剤又は分散剤の濃度や使用量が、前記の範囲内になるように用いれば良い。また、アルカリ剤及び分散剤を併用することもできる。 The alkali agent or dispersant is not only dissolved in water and used as an aqueous solution, but the alkali agent or dispersant and water may be separately added to the soil and mixed, or the alkali agent or dispersant may be added to the soil containing water. You may mix. In any case, the alkali agent or the dispersant may be used so that the concentration and the amount used thereof fall within the above ranges. Moreover, an alkali agent and a dispersing agent can also be used together.
現位置で、分散剤と水を別々に加える場合、例えば、分散剤の施用には肥料撒布機などを用いることができる。水は、通常水田に導水する方法により、加えることができる。 When the dispersant and water are added separately at the current position, for example, a fertilizer spreader can be used to apply the dispersant. Water can usually be added by a method of conducting water to paddy fields.
また、アルカリ剤又は分散剤を水溶液として加える場合には、例えば、タンクを用いてアルカリ剤又は分散剤を水に溶解し、所定の濃度になるよう混合した後、肥料散布機等を用いて施用できるほか、所定濃度より高濃度の溶液を調製して施用した後、所定濃度になるように水を加えても良い。また、導水時に連続的に薬剤を投入できる装置により施用しても良い。 In addition, when adding an alkaline agent or dispersant as an aqueous solution, for example, dissolve the alkaline agent or dispersant in water using a tank and mix them to a predetermined concentration, then use a fertilizer spreader or the like. In addition, after preparing and applying a solution having a concentration higher than a predetermined concentration, water may be added so as to obtain a predetermined concentration. Moreover, you may apply with the apparatus which can throw in a chemical | medical agent continuously at the time of water conveyance.
水（又はアルカリ剤若しくは分散剤水溶液）を導入後、導入した水と土壌表面を攪拌する。撹拌は、例えば、フロート式のプロペラ攪拌機や、チェーン攪拌機等を用いて行なうことができる。
攪拌は、土壌表面、特に土壌表面１〜５cm程度を攪拌するのが、効率良く土壌を浄化することができるので好ましい。
土壌表面を攪拌することにより、土壌粒子を水中に分散させ、懸濁状態とする。
After introducing water (or alkaline agent or dispersant aqueous solution), the introduced water and the soil surface are agitated. Stirring can be performed using, for example, a float type propeller stirrer or a chain stirrer.
For stirring, it is preferable to stir the soil surface, particularly about 1 to 5 cm, since the soil can be efficiently purified.
By stirring the surface of the soil, the soil particles are dispersed in water to be in a suspended state.
本発明においては、上記のように土壌表面に水を導入する前に、土壌表面が湿潤される程度に水を加えて放置するのが好ましく、表面の粗大な土塊を崩壊させることができる。また、アルカリ剤又は分散剤を含有する水を用いて浄化する場合に、下部の土壌への影響を抑えることができる。 In the present invention, before introducing water to the soil surface as described above, it is preferable to add water to such an extent that the soil surface is moistened and leave the soil surface, so that the coarse soil mass on the surface can be collapsed. Moreover, when purifying using the water containing an alkaline agent or a dispersing agent, the influence on the lower soil can be suppressed.
土壌表面の土壌粒子を懸濁状態とした後、放置して、土壌を粒径別に分級させる。放置時間は、土壌により異なるが、１〜１００分間、特に１〜４５分間程度放置するのが好ましい。この間に、土壌粒子のうち、粗粒子画分の粒子が土壌表面に沈降する。このような粗粒子は、放射性物質含量が低いため、そのまま土壌に戻すことにより、土壌損失量を低減することができる。 After making the soil particles on the soil surface in a suspended state, the soil particles are allowed to stand and are classified according to particle size. The standing time varies depending on the soil, but it is preferably left for 1 to 100 minutes, particularly about 1 to 45 minutes. During this time, of the soil particles, the coarse particle fraction particles settle on the soil surface. Since such a coarse particle has a low radioactive substance content, returning to the soil as it is can reduce the amount of soil loss.
上記のように放置した後、放射性物質含量の高い細粒子画分を除去する。細粒子画分を除去する方法は特に制限されないが、細粒子画分が、細粒子画分を含む土壌懸濁液である場合には、それを排水すれば良い。また、分級後の細粒子画分を、ユンボ、バックホー、ホイルローダー等を用いて、薄くはぎ取っても良い。
排水は、水田の場合、通常水田で落水する時開く排水口を開けて排水し、一時的にピットに貯留し、その後ポンプで廃水処理設備に入れても良いし、そのままポンプで水田から排水しても良い。
After leaving as above, the fine particle fraction having a high radioactive substance content is removed. The method for removing the fine particle fraction is not particularly limited, but when the fine particle fraction is a soil suspension containing the fine particle fraction, it may be drained. Further, the fine particle fraction after classification may be thinly peeled off using a yumbo, a backhoe, a wheel loader or the like.
In the case of paddy fields, drainage is usually performed by opening the drain opening that is opened when water is dropped in the paddy field, temporarily storing it in the pit, and then putting it into a wastewater treatment facility with a pump, or draining it from the paddy field as it is. May be.
このような処理を、少なくとも１回、好ましくは１〜５回行うことにより、放射能汚染土壌を浄化することができる。 By performing such treatment at least once, preferably 1 to 5 times, the radioactively contaminated soil can be purified.
排水された細粒子画分を含む土壌懸濁液は、凝集剤を加えた沈殿、ベルトプレスやフィルタープレス等や、これらの手法を組み合わせて、細粒子をオンサイトで回収することができる。 The soil suspension containing the drained fine particle fraction can collect fine particles on-site by precipitation using a flocculant, a belt press or a filter press, or a combination of these techniques.
次に、実施例を挙げて本発明をさらに詳細に説明するが、本発明はこれらに何ら制限されるものではない。 EXAMPLES Next, although an Example is given and this invention is demonstrated further in detail, this invention is not restrict | limited to these at all.
実施例１
現地ミニカラムにおける放射能汚染土壌の浄化を、以下の方法に従って行った。
(1)放射性セシウム（１３７Ｃｓ）で汚染された水田に、φ３０cm×Ｈ４５cmの円筒形ステンレスカラムを３連で耕盤まで打ち込み、土壌表面がひたひたとなるように土壌用水を加え、放置した。
(2)土壌表面が充分湿潤した後、水深１０cmとなるように用水を加え、１Ｍ水酸化ナトリウムを加えてｐＨを約９．５とした。
(3)土壌表面に撹拌羽をセットし、攪拌機で３０秒×３回撹拌する。
(4)撹拌後４５分放置した。この放置時間は完全分散条件で６μｍの粒子が１０cm沈降する時間である。放置後、サイホンで懸濁水を排水した。
(5)(1)〜(4)の手順を４回繰り返した後、土壌採取用のコアサンプラーをミニカラムの中心に耕盤まで打ち込み、土壌カラムを採取した。
(6)土壌カラム除去後の残土を耕盤まで採取した。
(7)採取した土壌および排水懸濁液中の１３７Ｃｓ含量および土壌微粒子含量を測定した。
Example 1
The purification of the radioactively contaminated soil in the local minicolumn was performed according to the following method.
(1) In a paddy field contaminated with radioactive cesium (137Cs), a cylindrical stainless steel column having a diameter of 30 cm × H45 cm was driven in triplicate to a tiller, and soil water was added so that the soil surface was trapped and allowed to stand.
(2) After the soil surface was sufficiently wet, water was added to a depth of 10 cm, and 1M sodium hydroxide was added to adjust the pH to about 9.5.
(3) Set a stirring blade on the soil surface and stir for 30 seconds x 3 times with a stirrer.
(4) The mixture was left for 45 minutes after stirring. This standing time is the time for which 6 μm particles settle to 10 cm under complete dispersion conditions. After standing, the suspended water was drained with a siphon.
(5) After repeating the procedures of (1) to (4) four times, the core sampler for soil collection was driven to the tiller at the center of the minicolumn, and the soil column was collected.
(6) The residual soil after removing the soil column was collected up to the tiller.
(7) 137Cs content and soil fine particle content in the collected soil and drainage suspension were measured.
処理後の土壌及び排水懸濁液中の１３７Ｃｓ含量は、ゲルマニウム半導体検出器で測定した。また、除去量合計／（除去量合計＋除去処理後の土壌）から、除去率（％）を求めた。
土壌表面撹拌後の排水懸濁液及び除去処理後の土壌中に含まれる１３７Ｃｓ含量を表１に示す。
The 137Cs content in the treated soil and drainage suspension was measured with a germanium semiconductor detector. Moreover, the removal rate (%) was calculated from the total removal amount / (total removal amount + soil after removal treatment).
Table 1 shows the 137Cs content contained in the drainage suspension after the soil surface stirring and the soil after the removal treatment.
表１の結果より、撹拌処理回数の増加に伴い、排水される１３７Ｃｓ量の低減が認められた。
また、土壌撹拌処理土と無処理土の作土（カラム周辺から採取した作土、３連）の１３７Ｃｓ濃度を比較すると、低減率は７１％となった（表２）。
なお、除去量合計は、No.３処理区で最も高い値を示しているが、撹拌終了後の目視では、撹拌羽の位置が３連処理の中で土壌表面に最も近接しており、１３７Ｃｓを高濃度に含む表面土壌の巻き上げが効率的に行えたと推察される。
From the results in Table 1, it was confirmed that the amount of 137Cs drained was reduced as the number of stirring treatments increased.
Moreover, when the 137Cs density | concentration of the soil of soil mixing process soil and untreated soil (the soil collected from the column periphery, 3 series) was compared, the reduction rate became 71% (Table 2).
Although the total removal amount shows the highest value in the No. 3 treatment section, the position of the stirring blade is closest to the soil surface in the triple treatment by visual inspection after the stirring is completed, and 137 Cs. It is inferred that the surface soil containing a high concentration of can was efficiently wound up.
また、作土に対する懸濁排水中に含まれる土壌微粒子の割合（土壌損失率）を算出した結果を、表３に示す。 In addition, Table 3 shows the results of calculating the ratio of soil fine particles (soil loss rate) contained in the suspended drainage to the soil.
作土全体に対する最終的な土壌損失量は処理区の作土厚によって異なるが、２〜４％程度となった。この値は面積換算すると、１０アール当たり５〜７トン程度の土壌排出量であり、仮比重を１としたときの土壌厚さで換算すると、約５〜７mmの土壌が排出されたことになる。浄化処理に伴う土壌排出量を抑制することができる。 The final amount of soil loss for the entire soil varies depending on the soil thickness of the treated area, but is about 2 to 4%. This value is about 5 to 7 tons per 10 ares in terms of area, and about 5 to 7 mm of soil was discharged when converted to the soil thickness when the temporary specific gravity is 1. . Soil emissions associated with purification treatment can be suppressed.
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