JP2000338295A - Cement material for solidifying liquid waste in reactor - Google Patents

Cement material for solidifying liquid waste in reactor

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Publication number
JP2000338295A
JP2000338295A JP11146133A JP14613399A JP2000338295A JP 2000338295 A JP2000338295 A JP 2000338295A JP 11146133 A JP11146133 A JP 11146133A JP 14613399 A JP14613399 A JP 14613399A JP 2000338295 A JP2000338295 A JP 2000338295A
Authority
JP
Japan
Prior art keywords
cement
drum
solidified
liquid waste
vermiculite
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
Application number
JP11146133A
Other languages
Japanese (ja)
Inventor
Katsuji Nagashima
勝治 永嶋
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.)
OOSUI KOSAN KK
Original Assignee
OOSUI KOSAN KK
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 OOSUI KOSAN KK filed Critical OOSUI KOSAN KK
Priority to JP11146133A priority Critical patent/JP2000338295A/en
Publication of JP2000338295A publication Critical patent/JP2000338295A/en
Pending legal-status Critical Current

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  • Curing Cements, Concrete, And Artificial Stone (AREA)

Abstract

PROBLEM TO BE SOLVED: To prevent harmful interstices from appearing when a liquid waste is solidified in a drum and the like by setting the radio between vermiculite and cement at a specific value and further using a cement compounding ingredient mixed with a specific percentage of a prescribed inflating agent. SOLUTION: A cement material used in order to solidify a radioactively contaminated liquid waste and the like is a mixture of Portland cement and vermiculite, for example. As to the weight ratio between vermiculite and Portland cement, the former is set at 0.5 to 1.5 and the latter at 7 to 9. This cement material is mixed with an inflating agent of 3 to 5 wt.% obtained by burning and crushing lime, plaster, bauxite and so on to make a solidified material. Then, it is filled into a drum, for example, until is occupies 90% of the internal space of the drum, and a used resin fat elution liquid waste is infiltrated as a reactor liquid waste through a strainer and is cured for a prescribed days. In the generated solidified waste which has sufficient strength, a good value is also shown in the judgement of an interstice between the solidified waste and the drum by a supersonic propagation velocity.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、原子力発電所など
から排出される放射能汚染の廃液(以下において使用済
樹脂溶離廃液とも称す)を固化するために使用するセメ
ント固化剤に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a cement solidifying agent used for solidifying radioactively contaminated waste liquid (hereinafter also referred to as spent resin elution waste liquid) discharged from a nuclear power plant or the like.

【0002】[0002]

【従来の技術】従来より、上記の放射能汚染廃液はドラ
ム缶の中に投入したセメントに含浸させて固化し、これ
を例えば六か所村に貯蔵することが行われている。
2. Description of the Related Art Conventionally, the above-mentioned radioactive waste liquid has been impregnated with cement put in a drum can and solidified, and this is stored in, for example, six locations.

【0003】[0003]

【発明が解決しようとする課題】上記の用途に使用され
る金属製ドラム缶は、その内面をコンクリートで被覆し
た、いわゆる内張のものである。そのドラム缶内に未硬
化のセメント粉末を充填し、そこに上記使用済樹脂溶離
廃液を注ぎ込み、該セメントに吸液せしめて固化するも
のであるが、このようにして凝固した固化体はドラム缶
内において収縮をなし、缶壁または前記の内張部内面と
の間に間隙を生じることになる。
The metal drum used for the above-mentioned applications is a so-called metal lining in which the inner surface is covered with concrete. The uncured cement powder is filled in the drum, and the used resin elution waste liquid is poured into the drum, and the solid is absorbed by the cement and solidified. Shrinkage will occur, creating a gap between the can wall and the inner surface of the lining.

【0004】放射能に汚染された諸々の物を貯留する六
か所村などにおいて、前記の廃液を固化封入したドラム
缶を受け入れるに際しては、内容物が完全に固化してい
るか、有害な空隙が残存していないかを知る手段とし
て、缶壁より内容物を通して反対側に達するまでの超音
波の伝播速度を測定する方法が採られているが、ドラム
缶と固化物との間に間隙が存在する(図5参照)と超音
波は内容物を通過することなく缶壁を迂回することにな
り、内容物の正確な性状が判定できず、該廃棄物の受け
入れが拒絶されることになる。
[0004] In a place such as Rokkasho, which stores various substances contaminated with radioactivity, when the drum containing solidified waste liquid is received, the contents are completely solidified or harmful voids remain. As a means of knowing whether or not the ultrasonic wave has propagated, the method of measuring the propagation speed of the ultrasonic wave from the can wall to the opposite side through the contents has been adopted, but there is a gap between the drum and the solidified material ( (See FIG. 5) and the ultrasonic waves bypass the can wall without passing through the contents, and the exact nature of the contents cannot be determined, and the acceptance of the waste is refused.

【0005】[0005]

【課題を解決するための手段】放射能汚染の廃液を吸収
したセメント材料を無収縮の状態で固体化させるための
固化材として、バーミキュライト:セメントを0.5〜
1.5:7〜9(重量比)とし、さらに膨張剤をそのセ
メントの3〜5重量%混合したセメント配合材とし、こ
れをドラム缶内に投入して、ここに前記の廃液を注入し
固化体とする手段を採用した。この場合のセメントは普
通セメント、例えばボルトランドセメントでよい。
As a solidifying material for solidifying the cement material having absorbed the radioactively contaminated waste liquid in a non-shrinking state, vermiculite: cement is used in an amount of 0.5 to 50%.
1.5: 7 to 9 (weight ratio), and a cement compounded material in which an expanding agent is mixed with 3 to 5% by weight of the cement, put into a drum can, and inject the waste liquid therein to solidify The body was adopted. The cement in this case may be ordinary cement, for example boltland cement.

【0006】ここに、膨張剤として石灰、石膏、ボーキ
サイトを主成分とする焼成化合物を粉砕したものを使用
する。これには、JIS A 6202に規定するコン
クリート用膨張剤が含まれる。この膨張剤を前記セメン
トに適量添加することによってコンクリートの乾燥によ
る収縮を抑制し、かつ、コンクリートの長期硬度を増大
せしめると共に水密性の向上が得られる。
[0006] Here, a sintering agent obtained by pulverizing a calcined compound mainly composed of lime, gypsum and bauxite is used. This includes a concrete expanding agent specified in JIS A6202. By adding an appropriate amount of this expanding agent to the cement, shrinkage due to drying of the concrete is suppressed, the long-term hardness of the concrete is increased, and the watertightness is improved.

【0007】[0007]

【発明の実施の形態】本発明の実施の形態について図表
を参照して説明する。本発明において使用するセメント
は前記のボルトランドセメントとバーミキュライトの混
合物で、バーミキュライトセメントと称するものであっ
て、その重量比をバーミキュライト0.5〜1.5に対
してボルトランドセメントを7〜9とした。このセメン
ト材料に、表1に示す膨張剤を該セメントの3〜5重量
%を添加混合した。以後、バーミキュライトセメント及
びこれに膨張剤を混合したものを固形化材料と称する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiments of the present invention will be described with reference to the drawings. The cement used in the present invention is a mixture of the above-mentioned bolt land cement and vermiculite, which is referred to as vermiculite cement, and the weight ratio is 0.5 to 1.5 of vermiculite and 7 to 9 of bolt land cement. did. To this cement material, a swelling agent shown in Table 1 was added and mixed in an amount of 3 to 5% by weight of the cement. Hereinafter, the vermiculite cement and the mixture of the vermiculite cement and the expanding agent are referred to as a solidified material.

【0008】[0008]

【表1】 [Table 1]

【0009】[0009]

【実施例】本発明に係る固形化材料の原子炉廃液固化の
性能を実施例によって説明する。まず、原子炉廃液とし
ての使用済樹脂溶離廃液に関しては、ぼう硝13.8
g、塩化アンモニュウム0.45gを水1リットル中に
混合攪拌した溶液を模擬廃液Rとして使用した。
EXAMPLES The performance of the solidification material according to the present invention for solidifying the waste liquid of a reactor will be described with reference to examples. First, with regard to the spent resin elution waste liquid as the reactor waste liquid, sodium nitrate 13.8 is used.
g, ammonium chloride 0.45 g was mixed and stirred in 1 liter of water and used as a simulated waste liquid R.

【0010】固形化材料として以下の5種類のものを用
い、その固化による膨脹または収縮性とその経時変化、
一軸圧縮強度を検討した。
[0010] The following five types of solidified materials are used, and their expansion or shrinkage due to solidification and their changes over time,
The uniaxial compressive strength was studied.

【0011】実験用の固形化材料(供試体) No.1 VC100% No.2 VC95%+CSA5% No.3 VC90%+CSA10% No.4 VC85%+CSA15% No.5 VC80%+CSA20% (VC:バーミキュライトセメント CSA:コンク
リート膨張剤)
The solidified material for the experiment (test sample) 1 VC 100% No. 1 No. 2 VC95% + CSA5% No. 3 VC90% + CSA10% No. 3 No. 4 VC85% + CSA15% 5 VC 80% + CSA 20% (VC: vermiculite cement CSA: concrete expanding agent)

【0012】固形化材料の膨脹及び収縮の予備実験を図
1に示す容器を用いて行った。すなわち、ドラム缶を模
した直径120mmの円筒状容器Cに前記のNo.1か
らNo.5の固形化材料Mを100mmの高さにまで充
填し、前記の模擬樹脂溶離廃液Rを自然浸透させ、28
日間の養生期間における膨脹収縮状況を測定した。その
結果、No.1およびNo.2は外観上の変形が見られ
なかったが、No.3からNo.5は順次膨脹が大きく
型枠が膨れる(図1参照)と共に固化体表面にひび割れ
を生じ、実用に適しないことがわかった。これらのう
ち、比較的良好なNo.1およびNo.2における膨脹
および収縮の経時変化を図2に示した。
Preliminary experiments on expansion and contraction of the solidified material were performed using the container shown in FIG. That is, in the cylindrical container C having a diameter of 120 mm simulating a drum can, the above-mentioned No. No. 1 to No. The solidified material M of No. 5 was filled to a height of 100 mm, and the simulated resin elution waste liquid R was allowed to naturally penetrate,
The state of expansion and contraction during the curing period of one day was measured. As a result, no. 1 and No. No. 2 did not show any deformation in appearance, 3 to No. 5 was found to be unsuitable for practical use because the expansion was large and the mold swelled (see FIG. 1) and the surface of the solidified body was cracked. Among these, comparatively good No. 1 and No. FIG. 2 shows the time-dependent changes in expansion and contraction in Sample No. 2.

【0013】そこで、No.1およびNo.2のCSA
比率になる固形化材料と 供試体No.6としてVC9
7%+CSA3% 配合の固形化材料を加えた3種類を
用いてドラム缶による実証実験を行った(図3)。この
場合、ドラム缶12にはコンクリートによって5cmの
内張13をしたものと内張のないものとを使用し、そこ
に固形化材料M(11)をドラム内容積の90%まで充
填し、ストレーナー14を介して模擬使用済樹脂溶離廃
液Rを浸透させ固形化を図った。
Therefore, No. 1 and No. 2 CSA
The solidified material and the specimen No. VC9 as 6
Demonstration experiments using drums were performed using three types, each containing a solidified material of 7% + CSA 3% (FIG. 3). In this case, a drum 12 having a lining 13 of 5 cm made of concrete and a lining 13 having no lining are used, and the solidified material M (11) is filled up to 90% of the inner volume of the drum, and the strainer 14 is used. Simulated spent resin elution waste liquid R was permeated through to achieve solidification.

【0014】固化後、ドラム缶と固化体との間の間隙の
有無をドラム缶の外径の一方から該缶の中心を挟む対向
側表面までの超音波伝播速度を測定することにより、ま
た、圧縮強度は上記の固形化材料により得られた固化体
を直径50mm、高さ100mmにコアボーリングして
一軸圧縮強度を測定することによって求めた。固形化材
料(供試体)とドラム缶の組み合わせにおける測定値を
表2に示した。
After solidification, the presence or absence of a gap between the drum and the solidified body is determined by measuring the ultrasonic wave propagation velocity from one of the outer diameters of the drum to the opposing surface sandwiching the center of the drum. Was determined by core boring a solidified body obtained from the above solidified material to a diameter of 50 mm and a height of 100 mm and measuring the uniaxial compressive strength. Table 2 shows the measured values of the combination of the solidified material (test sample) and the drum.

【0015】表2において、(1)の超音波伝播速度
は、内張なしのドラム缶単体のそれとほぼ同等の値を示
している。これは固化体とドラム缶との間に間隙が存在
するために超音波が固化体内を伝播することができず、
ドラム缶の周壁を伝播したものと考えられる。また、
(4)における超音波伝播速度は内張ドラム缶単体の超
音波伝播速度より小さい値を示しているがCSA5%添
加の(5)の伝播速度よりも遅く、したがってこの
(4)においては内張との間に僅かながら隙間を生じて
缶壁または内張に回避し伝播しているものである。
In Table 2, the ultrasonic wave propagation velocity of (1) shows a value substantially equal to that of the drum can without lining. This is because ultrasonic waves cannot propagate in the solidified body because there is a gap between the solidified body and the drum can,
It is probable that it propagated along the peripheral wall of the drum. Also,
The ultrasonic wave propagation velocity in (4) shows a value smaller than the ultrasonic wave propagation velocity of the lined drum alone, but is lower than the propagation velocity of (5) with addition of 5% CSA. There is a slight gap between them to avoid and propagate to the can wall or lining.

【0016】[0016]

【表2】 [Table 2]

【0017】CSA3%の配合の固形化材料(No.
6)における超音波の伝播は、ドラム缶に内張を施した
もの、施さないもの共に供試体No.1のそれより小さ
く(速く)、供試体No.2より大きな(遅い)値が得
られた。したがって、膨張剤の添加量は5%前後が望ま
しく、3ないし6%添加も実用に耐えるものと考えられ
る。
A solidified material (No.
The propagation of the ultrasonic wave in the sample No. 6) was carried out for both the drum with and without the lining. Specimen no. Values greater than 2 (slower) were obtained. Therefore, the addition amount of the swelling agent is desirably about 5%, and it is considered that the addition of 3 to 6% is also practical.

【0018】また、一軸圧縮強度は、汚染廃液処理に関
する科学技術庁告示第2号に規定された「固形化された
放射性廃棄物の一軸圧縮強度」(15kg/cm)を
十分に上回る値が得られた。
The unconfined compressive strength should be a value sufficiently higher than the "unconfined compressive strength of solidified radioactive waste" (15 kg / cm 2 ) specified in the Science and Technology Agency Notification No. 2 concerning the treatment of polluted waste liquid. Obtained.

【0019】また、固形化材料および模擬樹脂溶離廃液
を含浸して1ヶ月後および13ヶ月後にドラム缶を軸方
向に切断してドラム缶と固化体との間に間隙が存すか否
かを目視によって観察したが、明確な判定ができなかっ
た。したがって、膨張剤の添加量の最適値の決定は前記
の超音波伝播速度による判定によって行った。
Also, one month and 13 months after impregnating the solidified material and the simulated resin elution waste liquid, the drum can is cut in the axial direction, and it is visually observed whether or not a gap exists between the drum and the solidified body. However, a clear judgment could not be made. Therefore, the optimum value of the amount of the swelling agent was determined by the above-described determination based on the ultrasonic wave propagation speed.

【0020】さらに、種々の追加の実証試験から、VC
98%+CSA2%ないしVC94%+CSA6%(い
ずれも重量%)が超音波の伝播速度計測および圧縮強度
において良好であり、最も望ましくはVC96%+CS
A4%(重量%)の配合比率であることがわかった。
Further, from various additional demonstration tests, VC
98% + CSA2% to VC94% + CSA6% (all by weight%) are good in ultrasonic wave propagation velocity measurement and compressive strength, most preferably VC96% + CS
It was found that the mixing ratio was A4% (% by weight).

【0021】[0021]

【発明の効果】バーミキュライトセメントに石灰、石
膏、ボーキサイトを主成分とする焼成化合物を粉砕した
膨張剤を3〜6%混入した固形化材料をドラム缶に充填
し、これに放射能汚染の廃液を含浸させ固化すると、収
縮が押さえられて当該廃棄物の処分条件、すなわち、缶
内において有害な空隙を生じない結果が得られた。
According to the present invention, a drum can is filled with a solidified material obtained by mixing a vermiculite cement with an expanding agent obtained by pulverizing a calcined compound mainly composed of lime, gypsum and bauxite by 3 to 6%, and impregnated with radioactive waste liquid. Upon solidification, the shrinkage was suppressed and the waste was disposed of under the disposal conditions, that is, a result in which no harmful voids were formed in the can.

【図面の簡単な説明】[Brief description of the drawings]

【図1】固形化材料に模擬液を含浸させて固化体する装
置と、膨脹収縮を戯画的に示した断面表示の正面図であ
る。
FIG. 1 is a front view of a device for impregnating a solidified material with a simulated liquid to solidify the solidified material, and a cross-sectional view showing the expansion and contraction in a pictorial manner.

【図2】固形化材料No.1,No.2による固化体の
外径変化を表すグラフである。
FIG. 1, No. 4 is a graph showing a change in outer diameter of a solidified body due to No. 2.

【図3】ドラム缶を使用した実証実験装置を示した断面
表示の正面図である。
FIG. 3 is a front view of a sectional display showing a demonstration test apparatus using a drum.

【図4】膨張剤の添加量と圧縮強度の関係を示したグラ
フである。
FIG. 4 is a graph showing the relationship between the amount of expansion agent added and the compressive strength.

【図5】放射能汚染の廃液をドラム缶中にて固形化する
一般的な方法を示した中央断面の正面図である。
FIG. 5 is a front view of a central section showing a general method of solidifying radioactive waste liquid in a drum.

【符号の説明】[Explanation of symbols]

11 固形化材料 12 ドラム缶 13 コンクリート内張 14 ストレーナー Reference Signs List 11 solidified material 12 drum 13 concrete lining 14 strainer

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】バーミキュライト:セメントの重量比を
0.5〜1.5:7〜9とし、これに膨張剤をそのセメ
ントの3〜5重量%混合したことを特徴とする原子炉等
から排出される放射能汚染廃液の固化用セメント材料。
A weight ratio of vermiculite to cement of 0.5 to 1.5: 7 to 9 and an expansive agent mixed with 3 to 5% by weight of the cement are discharged from a nuclear reactor or the like. Material for solidification of waste radioactive waste.
【請求項2】膨張剤はCaO(50.0〜53.6
%)、Al(12.0〜15.0)、SO(2
7.0〜31.0)を主成分とするコンクリート用膨張
剤であることを特徴とする請求項1記載の放射能汚染廃
液の固化用セメント材料。
2. The swelling agent is CaO (50.0 to 53.6).
%), Al 2 O 3 (12.0 to 15.0), SO 3 (2
7. The cement material for solidifying radioactively contaminated waste liquid according to claim 1, which is an expanding agent for concrete containing 7.0 to 31.0) as a main component.
JP11146133A 1999-05-26 1999-05-26 Cement material for solidifying liquid waste in reactor Pending JP2000338295A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11146133A JP2000338295A (en) 1999-05-26 1999-05-26 Cement material for solidifying liquid waste in reactor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11146133A JP2000338295A (en) 1999-05-26 1999-05-26 Cement material for solidifying liquid waste in reactor

Publications (1)

Publication Number Publication Date
JP2000338295A true JP2000338295A (en) 2000-12-08

Family

ID=15400899

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11146133A Pending JP2000338295A (en) 1999-05-26 1999-05-26 Cement material for solidifying liquid waste in reactor

Country Status (1)

Country Link
JP (1) JP2000338295A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110491537A (en) * 2019-06-20 2019-11-22 中国辐射防护研究院 A kind of cement solidification processing method of radioactive waste
CN112321239A (en) * 2020-11-20 2021-02-05 佛山市睿德建筑节能材料有限公司 Ceramic tile glue and preparation method thereof

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110491537A (en) * 2019-06-20 2019-11-22 中国辐射防护研究院 A kind of cement solidification processing method of radioactive waste
CN110491537B (en) * 2019-06-20 2023-06-23 中国辐射防护研究院 Cement curing treatment method for radioactive waste
CN112321239A (en) * 2020-11-20 2021-02-05 佛山市睿德建筑节能材料有限公司 Ceramic tile glue and preparation method thereof
CN112321239B (en) * 2020-11-20 2022-03-08 佛山市睿德建筑节能材料有限公司 Ceramic tile glue and preparation method thereof

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