JPS621670B2 - - Google Patents
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- Publication number
- JPS621670B2 JPS621670B2 JP57091091A JP9109182A JPS621670B2 JP S621670 B2 JPS621670 B2 JP S621670B2 JP 57091091 A JP57091091 A JP 57091091A JP 9109182 A JP9109182 A JP 9109182A JP S621670 B2 JPS621670 B2 JP S621670B2
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- Prior art keywords
- water
- cement
- mud
- amount
- muddy water
- 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
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- Soil Conditioners And Soil-Stabilizing Materials (AREA)
Description
この発明は地中連続壁工法や泥水シールド工法
などの泥水工法に用いられる泥水に関する。
地中連続壁工法などに用いられる泥水として
は、従来よりベントナイトを主体としたベントナ
イト泥水が知られている。このベントナイト泥水
は、水道水にベントナイト6〜8%(重量比、以
下同じ)を分散したものであり、造壁性に優れ、
多くの実績を有している。しかしながら、このベ
ントナイト泥水は、ベントナイトの特性の1つで
あるイオン交換能あるいは塩基置換能によつて、
土壌、地下水、海水、セメントなどから溶出する
各種イオンの影響(特に金属塩等のイオン)を受
け、劣化する欠点がある。特に、海水およびセメ
ントの混入は、ベントナイト泥水の安定性を著る
しく低下せしめる。このため、海水やセメントの
混入による安定性低下の対策として、カルボキシ
ルメチルセルロース(CMC)などの増粘剤やリ
グニンスルホン酸化合物やポリリン酸塩などの分
散剤が、それぞれ0.05〜0.3%程度添加されるこ
とがある。増粘剤は泥水の粘性を保持し、脱水量
を減少させる効果があり、分散剤は塩類混入によ
る劣化防止と混入土砂を沈降させ、泥水の比重、
粘性の増大を防止する効果がある。しかし、これ
らの増粘剤、分散剤の効果は十分とはいえず、塩
水(NaCl)が0.5〜0.7%、セメント成分が0.5〜
1%以上混入すると使用は不可能となる。ところ
が、施工現場では海水が1%以上混入する場合が
たびたびあり、またコンクリート打設時にはセメ
ント成分が最大5〜7%程度混入することがあ
り、上記増粘剤および分散剤の添加では劣化対策
として不十分であつた。
このため、海水成分やセメント成分の混入によ
つても劣化しないCMCなどを主体としたポリマ
ー泥水が使用されつつある。しかし、このポリマ
ー泥水は、夏期、CMCが腐敗劣化し、その機能
を失う欠点がある。また、掘削工法に掘削ピツト
を用いるロータリー掘削法を適用した場合には、
CMCが混入土砂と一緒に分離してしまい、CMC
を常に補充せねばならず、コストの面で不経済と
なつており、したがつて、ポリマー泥水も泥水工
法用泥水としては決して満足のゆくものではな
い。さらに、ベントナイト泥水では、Clイオン
やCaイオンを含まない良質の清水を用いて泥水
を製造せねばならないが、施工現場でこのような
良質の清水を入手することはだんだん不可能とな
つてきている。
この発明は、上記事情に鑑みてなされたもの
で、海水成分やセメント成分が高濃度に混入して
もゲル化せず、安定性を有し、その機能を充分維
持し、かつ良質の清水を必要とせず、川水、海
水、地下水などの低質水を用いて製造できる泥水
工法用泥水を提供することを目的とするものであ
る。
この発明の泥水は、少なくともベントナイト
と、Caイオンに対する錯化力が300mg/g以上の
ポリアクリル酸塩とを有することを特徴とするも
のである。
この発明に用いられるベントナイトとしては、
従来よりベントナイト泥水に用いられている通常
の粒度200〜350メツシユ程度のものが挙げられる
が、特に限定されるものではない。このベントナ
イトの混合量は、泥水に対し重量比4〜8%であ
り、通常は6%程度が好ましい。
また、Caイオンに対する錯化力が300mg/g以
上のアクリル酸塩としては、ポリアクリル酸のナ
トリウム塩、カリウム塩、アンモニウム塩および
モノエタノールアミン、ジエタノールアミン、ト
リエタノールアミン、ピリジン、ピペリジン、モ
ルホリンなどのアミン塩であつて、かつCaイオ
ンに対する錯化力が300mg/g以上のものであ
る。Caイオンに対する錯化力は、酢酸カルシユ
ウム水溶液の滴定法によつて求めたものである。
この錯化力が300mg/g未満のポリアクリル酸塩
では、海水成分およびセメント成分によるゲル化
を防止し、安定性を維持する効果がない。(第1
図10−Gelとセメント混入量の関係を示すグラ
フ参照)このポリアクリル酸塩の配合量は、泥水
に対して重量比で0.2〜2%、好ましくは0.4〜0.6
%である。(第2図参照)0.2%未満では上記安定
化効果が充分得られず、また2%を越えると泥水
の粘度が高くなりすぎ、混練が不可能となるとと
もに凝集性が表われて不都合となる。
さらに、この発明の泥水に用いられる水として
は、水道水などの良質の水に限られず、各種イオ
ンが含まれる地下水、川水、工業用水などの低コ
ストで調達の容易な低質の水を用いることができ
る。これは上記Caイオンに対する錯化力が300
mg/g以上のポリアクリル酸塩を用いることによ
つて、水中に含まれる各種イオンが錯化され、ベ
ントナイトとの反応が阻止されるためである。
この発明の泥水は、ベントナイトと上記特定の
ポリアクリル酸塩とで充分その機能を発揮する
が、必要に応じてこれに公知のCMCなどの増粘
剤やフミン酸塩、リグリンスルホン酸化合物、ヘ
キサメタリン酸塩、トリポリリン酸塩などの分散
剤を添加してもよい。増粘剤の添加量は泥水に対
して0.05〜0.3wt%、また分散剤の添加量は同じ
く0.05〜0.3wt%とされる。
以下、実施例を示して具体的に説明する。
実施例 1
ベントナイト6wt%、増粘剤としてCMC0.1wt
%、Caイオンに対する錯化力が340mg/gのポリ
アクリル酸ソーダ0.4wt%とからなる本発明の泥
水に、ポルトランドセメント分散液および塩化ナ
トリウム水溶液を加えて、泥水の性状の変化を検
討した。セメント分散液および塩化ナトリウム水
溶液の泥水への添加量は5wt%と一定とし、分散
液および水溶液の濃度を変えてセメント、塩化ナ
トリウムの濃度変化に対応する泥水性状の変化を
求めた。また、上記ポリアクリル酸ソーダに代え
てリグニンスルホン酸化合物および錯化力が260
mg/gのポリアクリル酸ソーダを同じく0.4wt%
添加した比較例についても同様の検討を行つた。
泥水の性状としては、PH測定(ガラス電極によ
る)、API規格加圧過試験による脱水量、VGメ
ータによるゲルストレングス(10−Gel)および
フアンネル粘度計を用いたフアンネル粘性FVを
求めた。
結果を第1図に示す。第1図は上から順に、セ
メントあるいはNaCl混入時における泥水のPHの
変化、脱水量の変化、ゲル化量の変化、粘性の変
化をそれぞれ示すものである。泥水の脱水量、ゲ
ル化量および粘性はいずれも低いほど有効であ
る。
第1図において10−Gelとセメント混入量の関
係をから明らかであるように、錯化力が300mg/
g以上のポリアクリル酸ソーダが配合された泥水
はセメント混入量が5wt%となつてもゲル化せ
ず、泥水としての機能を維持している。この結果
から、本発明の泥水は安定性に優れていることが
確認できた。
実施例 2
ベントナイト6wt%、増粘剤としてCMC0.1wt
%、Caイオンに対する錯化力が340mg/gのポリ
アクリル酸ソーダ0〜0.6wt%の泥水を製造し、
実施例1と同様にこれら泥水のゲルストレングス
(10−Gel)およびフアンネル粘性(FV)につい
て測定し、上記ポリアクリル酸ソーダの濃度の影
響を調べた。その結果を第2図に示す。第2図の
FV.とセメント混入量の関係から明らかなよう
に、錯化力300mg/g以上のポリアクリル酸ソー
ダが0.2%以上配合されるとセメント混入による
粘性の増加が確実に防止される。また、10−Gel
とセメント混入量の関係から明らかなように、ポ
リアクリル酸ソーダが0.4%以上配合されるとセ
メント混入による10−Gelの増加が確実に防止さ
れる。これからの結果から、上記特定の錯化力を
有するポリアクリル酸ソーダの濃度が0.2wt%以
上となると、ゲル化防止効果が表れはじめ、0.4
〜0.6wt%で十分な効果が得られることが判明し
た。
実施例 3
種々の泥水製造用水を用意し、これらの水を用
いて本発明の泥水を作成し、その性状、安定性に
ついて検討した。また、通常の泥水の2倍の濃度
の濃縮泥水を一旦作成し、この濃縮泥水を希釈す
る方法についても同時に検討した。結果を第1表
に示す。
第1表の結果から明らかなように、本発明の
Caイオンに対する錯化力が300mg/g以上のポリ
アクリル酸塩を用いることにより、セメント抽出
水や人工海水などのNaイオンやCaイオンを高濃
度に含む水を用いてもゲル化しない安定な泥水を
作成することができる。セメント抽出水を用いる
ことができることは実用上大きな効果となる。す
なわち、実際の施工においては、コンクリート打
設時、どうしても泥水がコンクリートと接触し、
従来の泥水では、コンクリート打設面から10m
The present invention relates to muddy water used in muddy water construction methods such as underground wall construction method and muddy water shield construction method. Bentonite mud, which is mainly composed of bentonite, has been known as mud water used in underground wall construction methods and the like. This bentonite mud water is made by dispersing 6 to 8% bentonite (weight ratio, the same below) in tap water, and has excellent wall-building properties.
We have many achievements. However, this bentonite slurry has ion exchange ability or base substitution ability, which is one of the characteristics of bentonite.
It has the disadvantage that it deteriorates due to the influence of various ions (especially ions from metal salts, etc.) leached from soil, groundwater, seawater, cement, etc. In particular, the contamination of seawater and cement significantly reduces the stability of bentonite mud. For this reason, as a measure to prevent stability deterioration due to contamination with seawater or cement, thickeners such as carboxymethyl cellulose (CMC) and dispersants such as lignin sulfonic acid compounds and polyphosphates are added at approximately 0.05 to 0.3% each. Sometimes. Thickeners have the effect of maintaining the viscosity of muddy water and reducing the amount of water dewatered, while dispersants prevent deterioration due to salt contamination, settle mixed soil, and reduce the specific gravity of muddy water.
It has the effect of preventing an increase in viscosity. However, the effects of these thickeners and dispersants are not sufficient, with salt water (NaCl) at 0.5-0.7% and cement components at 0.5-0.
If it is mixed in at a concentration of 1% or more, it becomes unusable. However, at construction sites, seawater often mixes in at 1% or more, and when concrete is poured, up to 5 to 7% of cement components may mix in. Adding the above-mentioned thickeners and dispersants is not effective as a countermeasure against deterioration. It was insufficient. For this reason, polymer slurry based on CMC, which does not deteriorate even when mixed with seawater or cement components, is being used. However, this polymer muddy water has the disadvantage that the CMC rots and deteriorates during the summer and loses its functionality. In addition, when applying the rotary excavation method using an excavation pit to the excavation method,
CMC is separated together with mixed soil and CMC
must be constantly replenished, making it uneconomical in terms of cost.Therefore, polymer slurry is also by no means satisfactory as slurry for muddy construction methods. Furthermore, bentonite mud must be manufactured using high-quality clean water that does not contain Cl ions or Ca ions, but it is becoming increasingly impossible to obtain such high-quality clean water at construction sites. . This invention was made in view of the above circumstances, and it does not gel even when seawater components or cement components are mixed in at high concentrations, has stability, sufficiently maintains its functions, and provides high-quality fresh water. The object of the present invention is to provide mud water for mud construction methods that can be produced using low-quality water such as river water, sea water, and ground water without the need for mud water. The muddy water of the present invention is characterized by containing at least bentonite and a polyacrylate having a complexing power for Ca ions of 300 mg/g or more. The bentonite used in this invention is
Examples include particles having a particle size of about 200 to 350 mesh, which have been conventionally used for bentonite mud, but are not particularly limited. The mixing amount of bentonite is 4 to 8% by weight of the muddy water, and usually about 6% is preferable. In addition, examples of acrylates with complexing power for Ca ions of 300 mg/g or more include sodium salts, potassium salts, ammonium salts of polyacrylic acid, monoethanolamine, diethanolamine, triethanolamine, pyridine, piperidine, morpholine, etc. It is an amine salt and has a complexing power for Ca ions of 300 mg/g or more. The complexing power for Ca ions was determined by titration of an aqueous calcium acetate solution.
A polyacrylate having a complexing power of less than 300 mg/g is ineffective in preventing gelation caused by seawater components and cement components and maintaining stability. (1st
(See Figure 10 - Graph showing the relationship between Gel and the amount of cement mixed in) The amount of polyacrylate added is 0.2 to 2% by weight, preferably 0.4 to 0.6% by weight of the muddy water.
%. (See Figure 2) If it is less than 0.2%, the above-mentioned stabilizing effect cannot be obtained sufficiently, and if it exceeds 2%, the viscosity of the muddy water becomes too high, making it impossible to knead and causing agglomeration, which is disadvantageous. . Furthermore, the water used for the muddy water of the present invention is not limited to high-quality water such as tap water, but also low-quality water that is easy to procure at low cost, such as groundwater, river water, and industrial water that contain various ions. be able to. This has a complexing power of 300 for the above Ca ions.
This is because by using a polyacrylate of mg/g or more, various ions contained in water are complexed and their reaction with bentonite is inhibited. The muddy water of this invention sufficiently exhibits its function with bentonite and the above-mentioned specific polyacrylate, but if necessary, it may be added with a known thickener such as CMC, humate, ligurin sulfonic acid compound, etc. A dispersant such as hexametaphosphate or tripolyphosphate may be added. The amount of the thickener added is 0.05 to 0.3 wt% with respect to the muddy water, and the amount of the dispersant added is also 0.05 to 0.3 wt%. Hereinafter, a specific explanation will be given by showing examples. Example 1 Bentonite 6wt%, CMC 0.1wt as thickener
A portland cement dispersion and an aqueous sodium chloride solution were added to the muddy water of the present invention consisting of 0.4wt% of sodium polyacrylate having a complexing power for Ca ions of 340mg/g, and changes in the properties of the muddy water were investigated. The amounts of cement dispersion and sodium chloride aqueous solution added to mud water were kept constant at 5 wt%, and the concentrations of the dispersion and aqueous solution were varied to determine changes in mud water properties corresponding to changes in the concentrations of cement and sodium chloride. In addition, in place of the above sodium polyacrylate, a lignin sulfonic acid compound and a complexing power of 260
mg/g sodium polyacrylate at 0.4wt%
A similar study was conducted for the comparative example in which the compound was added. The properties of the muddy water were determined by PH measurement (using a glass electrode), the amount of water removed by the API standard pressurization test, the gel strength (10-Gel) by a VG meter, and the Funnel viscosity FV using a Funnel viscometer. The results are shown in Figure 1. Figure 1 shows, from top to bottom, changes in PH, dewatering amount, gelation amount, and viscosity of mud water when cement or NaCl is mixed. The lower the dehydration amount, gelling amount, and viscosity of mud water, the more effective it is. As is clear from the relationship between 10-Gel and the amount of cement mixed in Figure 1, the complexing power is 300mg/
Mud water containing more than g of sodium polyacrylate does not gel even when the amount of cement mixed in is 5 wt%, and maintains its function as mud water. From this result, it was confirmed that the muddy water of the present invention has excellent stability. Example 2 Bentonite 6wt%, CMC 0.1wt as thickener
%, producing muddy water containing 0 to 0.6 wt% of sodium polyacrylate with a complexing power for Ca ions of 340 mg/g,
The gel strength (10-Gel) and funnel viscosity (FV) of these muddy waters were measured in the same manner as in Example 1, and the influence of the concentration of the sodium polyacrylate was investigated. The results are shown in FIG. Figure 2
As is clear from the relationship between FV. and the amount of cement mixed in, if 0.2% or more of sodium polyacrylate with a complexing power of 300 mg/g or more is mixed, an increase in viscosity due to cement mixed in can be reliably prevented. Also, 10−Gel
As is clear from the relationship between the amount of cement mixed in and the amount of cement mixed in, when sodium polyacrylate is blended in an amount of 0.4% or more, an increase in 10-Gel due to cement mixed in is reliably prevented. From the results, when the concentration of sodium polyacrylate having the above-mentioned specific complexing power is 0.2wt% or more, gelation prevention effect starts to appear, and 0.4wt% or more.
It was found that a sufficient effect can be obtained at ~0.6wt%. Example 3 Various waters for producing muddy water were prepared, muddy water of the present invention was prepared using these waters, and its properties and stability were investigated. At the same time, we also studied a method of creating concentrated mud with twice the concentration of normal mud and then diluting this concentrated mud. The results are shown in Table 1. As is clear from the results in Table 1, the present invention
By using polyacrylate with a complexing power for Ca ions of 300 mg/g or more, stable muddy water that does not gel even when using water containing high concentrations of Na and Ca ions, such as cement extraction water and artificial seawater, can be created. can be created. The ability to use cement extracted water has a great practical effect. In other words, in actual construction, when concrete is poured, muddy water inevitably comes into contact with the concrete.
In conventional muddy water, 10m from the concrete pouring surface.
【表】【table】
【表】【table】
【表】
以内の泥水を廃棄処分していたが、この発明の泥
水では廃棄する必要がなく、従来廃棄している泥
水を回収使用できることになる。また、一旦高濃
度の濃縮泥水を作成し、これを掘削泥水からの分
離水で希釈しても、良好な性状の泥水が得られる
ことがわかる。これによつても現場で発生する掘
削泥水分離水を有効利用できるとともに、高価で
入手困難な水道水の使用量を低減でき、施工費の
コストを大幅に低下できる。
以上説明したように、この発明の泥水工法用泥
水は、少なくともベントナイトと、Caイオンに
対する錯化力が300mg/g以上のポリアクリル酸
塩とを有してなるものであるので、海水成分やセ
メント成分が高濃度(NaCl分で3%、セメント
分5〜7%)に混入しても、ゲル化せず安定性を
保持する。したがつて従来にあつては、コンクリ
ート打設時にセメント成分が混入した結果廃棄せ
ざるを得なかつた泥水有効に再利用できるととも
に、廃棄処分費用が低減され、処理設備を小型化
できる。また、製造用水にコストが安く、調達が
容易な地下水、川水、掘削泥水分離水などを用い
ることができる。さらに、臨海埋立地などの塩分
の多い施工個所でも何んら問題なく施工できる。
さらに、CMCなどを主体とするポリマー泥水の
ように腐敗することがないとともに掘削機械の制
限を受けることがない。また、濃縮泥水を作成し
ておき、これを現場内で発生する掘削泥水分離水
などを用いて希釈することができるので、分離水
の有効利用ができるとともに、高価な水道水など
の良質水を節約できる。さらに、良質水を得難い
僻地で泥水工法を施工する場合にあつては、工事
現場に良質水を搬入する必要が無く、この点から
も建設コストの低減を図ることができる。さらに
また、泥水のゲル化がないので、泥水のゲル化に
起因する打設コンクリートの品質の低下が防止で
きるなどの実用上極めて大きな効果を有するもの
である。[Table] Previously, the muddy water within the range of 100 to 100 ml was disposed of, but the muddy water of this invention does not need to be disposed of, and the muddy water that was conventionally disposed of can be recovered and used. Furthermore, it can be seen that even if highly concentrated concentrated mud is once created and then diluted with water separated from drilling mud, mud with good properties can be obtained. This also makes it possible to effectively utilize the separated drilling mud water generated at the site, reduce the amount of tap water that is expensive and difficult to obtain, and significantly reduce construction costs. As explained above, the muddy water for the muddy construction method of the present invention contains at least bentonite and polyacrylate having a complexing power for Ca ions of 300 mg/g or more. Even when the ingredients are mixed in at high concentrations (NaCl content: 3%, cement content: 5-7%), it does not gel and maintains stability. Therefore, in the past, muddy water that had to be discarded as a result of being mixed with cement components during concrete placement can be effectively reused, disposal costs can be reduced, and processing equipment can be downsized. In addition, low-cost and easily procured groundwater, river water, separated water from drilling mud, etc. can be used as manufacturing water. Furthermore, it can be installed in areas with high salt content, such as coastal landfills, without any problems.
Furthermore, unlike polymer slurry made mainly of CMC, it does not rot and is not subject to the limitations of excavating machinery. In addition, it is possible to create concentrated mud water and dilute it using separated drilling mud water generated on-site, which allows for effective use of separated water and the use of high-quality water such as expensive tap water. You can save money. Furthermore, when using the muddy water construction method in remote areas where it is difficult to obtain good quality water, there is no need to bring good quality water to the construction site, and from this point of view as well, construction costs can be reduced. Furthermore, since there is no gelation of muddy water, it has extremely great practical effects, such as preventing deterioration in the quality of poured concrete due to gelation of muddy water.
第1図は上から順に本発明の泥水のセメント混
入下あるいは塩混入下におけるPH、脱水量、ゲル
化量、フアンネル粘性の変化を表すグラフ、第2
図は錯化力300mg/g以上のポリアクリル酸塩の
配合量を変えた場合セメントあるいは塩の混入量
とゲル化量およびフアンネル粘性の関係がどのよ
うに変化するかを示すグラフである。
FIG. 1 is a graph showing, from top to bottom, changes in PH, amount of dehydration, amount of gelling, and funnel viscosity in the muddy water of the present invention when mixed with cement or salt;
The figure is a graph showing how the relationship between the amount of cement or salt mixed in, the amount of gelation, and the funnel viscosity changes when the amount of polyacrylate with a complexing power of 300 mg/g or more is changed.
Claims (1)
とからなり、 上記ポリアクリル酸塩のCaイオンに対する錯
化力が300mg/g以上であつて、かつその配合量
が0.2〜2重量%であることを特徴とする泥水工
法用泥水。[Claims] 1. Comprised of at least bentonite and polyacrylate, the polyacrylate has a complexing power for Ca ions of 300 mg/g or more, and the blending amount is 0.2 to 2% by weight. Mud water for mud water construction method is characterized by certain characteristics.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9109182A JPS58208376A (en) | 1982-05-28 | 1982-05-28 | Mud water for mud water construction method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP9109182A JPS58208376A (en) | 1982-05-28 | 1982-05-28 | Mud water for mud water construction method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS58208376A JPS58208376A (en) | 1983-12-05 |
| JPS621670B2 true JPS621670B2 (en) | 1987-01-14 |
Family
ID=14016846
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP9109182A Granted JPS58208376A (en) | 1982-05-28 | 1982-05-28 | Mud water for mud water construction method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS58208376A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS61120881A (en) * | 1984-11-16 | 1986-06-07 | Shimizu Constr Co Ltd | Additive for drilling mud |
| CN1049236C (en) * | 1993-04-15 | 2000-02-09 | 华中理工大学 | Stabilizer for preventing clay expansion in oleaginous layer |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS554792B2 (en) * | 1973-09-20 | 1980-01-31 | ||
| JPS50158107A (en) * | 1974-06-11 | 1975-12-20 | ||
| JPS5827320B2 (en) * | 1975-06-30 | 1983-06-08 | 株式会社日本触媒 | Senzai Sosabutsu |
| JPS55104383A (en) * | 1979-02-07 | 1980-08-09 | Agency Of Ind Science & Technol | Dehydration quantity adjusting composition for sludge water in excavation |
-
1982
- 1982-05-28 JP JP9109182A patent/JPS58208376A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS58208376A (en) | 1983-12-05 |
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