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JPH10263313A - Regeneration of cleaning water for aggregate for concrete - Google Patents

Regeneration of cleaning water for aggregate for concrete

Info

Publication number
JPH10263313A
JPH10263313A JP7629697A JP7629697A JPH10263313A JP H10263313 A JPH10263313 A JP H10263313A JP 7629697 A JP7629697 A JP 7629697A JP 7629697 A JP7629697 A JP 7629697A JP H10263313 A JPH10263313 A JP H10263313A
Authority
JP
Japan
Prior art keywords
cmc
water
concrete
added
flocculant
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
JP7629697A
Other languages
Japanese (ja)
Inventor
Toshiaki Ichihara
俊昭 市原
Hiroyuki Sumiyama
弘行 角山
Iku Kaneko
郁 金子
Masakuni Kudo
正邦 工藤
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.)
Nippon Paper Industries Co Ltd
Jujo Paper Co Ltd
Original Assignee
Nippon Paper Industries Co Ltd
Jujo Paper 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 Nippon Paper Industries Co Ltd, Jujo Paper Co Ltd filed Critical Nippon Paper Industries Co Ltd
Priority to JP7629697A priority Critical patent/JPH10263313A/en
Publication of JPH10263313A publication Critical patent/JPH10263313A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
    • C04B18/04Waste materials; Refuse
    • C04B18/16Waste materials; Refuse from building or ceramic industry
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B22/00Use of inorganic materials as active ingredients for mortars, concrete or artificial stone, e.g. accelerators or shrinkage compensating agents
    • C04B22/002Water
    • C04B22/0026Salt water, e.g. seawater
    • C04B22/0033Salt water, e.g. seawater other than sea water, e.g. from mining activities
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Ceramic Engineering (AREA)
  • Civil Engineering (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Mining & Mineral Resources (AREA)
  • Inorganic Chemistry (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

PROBLEM TO BE SOLVED: To regenerate a cleaning water which gives no influence on the slump flow even when a flocculant deposits on crushed sand by subjecting a contaminated water produced in a cleaning process of an aggregate for a concrete to a treatment with carboxymethylcellulose and polyaluminum chloride so as to flocculate and precipitate the sludge, and then adding a cellulase to the supernatant. SOLUTION: A carboxymethylcellulose(CMC) is added to a contaminated water produced in a cleaning process of a crushed sand and the like so that the suspended substance which intrinsically has negative charges is further electrified into negative changes by the anionic property of the CMC. Then polyaluminum chloride(PAC) having positive charges is added to neutralize the charges so that even inorg. fine particles which can no be precipitated by the weak negative charges intrinsic to the inorg. suspended substance can be rapidly precipitated to clarify the contaminated water. When the recovered water contains CMC and PAC as the flocculant after the precipitate is separated, the flocculant affects the slump flow, therefore, a cellulase is added to decompose CMC. Thus, the regenerated cleaning water can be used to produced a good concrete.

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】本発明はコンクリート用骨材
として用いられる細骨材の製造において、山砂利、海砂
利、陸砂利、砕石などの原石を適度に破砕することによ
って得られる砕砂を水洗し、その後、水を含んだ含水砕
砂を取り出すという工程で製造される。
BACKGROUND OF THE INVENTION The present invention relates to a method for producing fine aggregate used as an aggregate for concrete, in which crushed sand obtained by appropriately crushing rough stones such as mountain gravel, sea gravel, land gravel and crushed stone is washed with water. Then, it is manufactured in a process of taking out crushed hydrous sand containing water.

【0002】本発明は、この際発生する汚泥水をコンク
リートの性状に影響を与えないように再生し再使用する
処理方法に関するものである。
[0002] The present invention relates to a treatment method for regenerating and reusing sludge water generated at this time without affecting the properties of concrete.

【0003】[0003]

【従来の技術】砕砂等を洗浄した際に発生する汚泥水
は、一般にポリアクリルアミド系の高分子凝集剤が添加
され泥状物を凝固、沈殿、分離させた後、回収再使用さ
れているが、この回収水に高分子凝集剤が残存している
と、これで洗浄した含水砕砂の中に取り込まれ、生コン
プラントでコンクリート製造時にスランプが出ないとい
う問題を起こす。
2. Description of the Related Art Sludge water generated when washing crushed sand or the like is generally recovered and reused after a polyacrylamide-based polymer flocculant is added to coagulate, precipitate, and separate the slurry. If the polymer flocculant remains in the recovered water, it will be taken into the hydrated crushed sand washed with this, causing a problem that slump does not appear during concrete production in a ready-mixed plant.

【0004】本発明はポリアクリルアミド系高分子凝集
剤の代わりに、カルボキシメチルセルロース(以下CM
Cと略)とポリ塩化アルミニウム(以下PACと略)で
汚泥水を処理した後に、セルラーゼを添加処理した回収
水で砕砂を洗浄することにより、含水砕砂に取り込まれ
た後、コンクリートに混入されてもコンクリートの性状
に影響の無い回収水の処理方法を提供するものである。
In the present invention, carboxymethylcellulose (hereinafter referred to as CM) is used instead of a polyacrylamide-based polymer flocculant.
C) and polyaluminum chloride (hereinafter abbreviated as PAC) to treat the sludge water, and then wash the crushed sand with the recovered water to which cellulase has been added. The present invention also provides a method for treating recovered water that does not affect the properties of concrete.

【0005】[0005]

【発明が解決しようとする課題】ポリアクリルアミド系
高分子凝集剤が、砕砂に付着したままで、コンクリート
に混入されると、高分子凝集剤が練り水に対して30ppm
以上の濃度になると、コンクリートのスランプフローに
影響を与えることが知られている。高分子凝集剤の標準
使用量は汚泥水に対して1〜4ppm (表面水5%と仮定
し、練り水に対し、0.5 〜1.0ppm)程度で、通常の使用
方法では全く問題はない。
When the polyacrylamide polymer flocculant is mixed with concrete while adhering to the crushed sand, the polymer flocculant becomes 30 ppm relative to the mixing water.
It is known that the above concentration affects the slump flow of concrete. The standard amount of the polymer coagulant used is about 1 to 4 ppm based on the sludge water (assuming that the surface water is 5%, and 0.5 to 1.0 ppm based on the kneading water), and there is no problem in the usual use method.

【0006】しかし、高分子凝集剤の溶解濃度は一般
に、1,000ppmに調製され汚泥水の流れているシュートに
溶解液を添加している。その溶解液の添加量はバルブ開
度でコントロールされている状態で、とても厳密に管理
されているとは言い難い。
However, the dissolution concentration of the polymer flocculant is generally adjusted to 1,000 ppm, and the solution is added to a chute in which sludge water flows. It is hard to say that the amount of the solution added is very strictly controlled in a state controlled by the valve opening.

【0007】また回収水が循環使用されているため、上
澄水の中でも、高分子凝集剤が累積され、更に洗浄され
た砕砂ヤード中での水分蒸発による高分子凝集剤の濃縮
化も懸念され、長い作業期間の中では、危険範囲に混入
されることが、充分に危惧される。
Further, since the recovered water is circulated, the polymer flocculant is accumulated in the supernatant water, and there is a concern that the polymer flocculant may be concentrated by evaporation of water in the washed crushed sand yard. During long working periods, there is a great concern that it will be included in the danger area.

【0008】本発明の目的は砕砂に凝集剤が付着しても
コンクリートのスランプフローに影響のない細骨材洗浄
水の再生方法を提供するものである。
An object of the present invention is to provide a method for regenerating fine aggregate washing water which does not affect the slump flow of concrete even if a flocculant adheres to crushed sand.

【0009】[0009]

【課題を解決するための手段】本発明者らは建設工事汚
濁水の清澄化方法として知られているCMC−PAC併
用凝集沈殿法(特公昭55−33672号公報)をこの
砕砂を洗浄した際に発生する汚濁水に応用し、CMCや
PACが細骨材中に混入された時の影響を詳細に検討し
た結果、CMC−PAC凝集沈殿法により得られた上澄
液にセルラーゼを添加処理することにより、凝集剤とし
て使用したCMCとPACがコンクリート中に混入され
てもコンクリートのスランプフローに影響が出ないこと
を見出し、本発明に至ったものである。
Means for Solving the Problems The present inventors have conducted a coagulation and sedimentation method using a combination of CMC and PAC (Japanese Patent Publication No. 55-33672), which is known as a method for clarifying polluted water in construction work, when washing the crushed sand. The cellulase was added to the supernatant obtained by the CMC-PAC coagulation sedimentation method as a result of a detailed study of the effects of CMC and PAC mixed in the fine aggregate, applied to the polluted water generated in the above. As a result, they found that even if CMC and PAC used as coagulants were mixed into concrete, the slump flow of concrete was not affected, and the present invention was reached.

【0010】すなわち、本発明の方法は、コンクリート
用骨材を洗浄した際に発生する汚濁水をまずCMCとP
ACで処理し、次いで汚泥分を凝集沈殿した上澄液にセ
ルラーゼを添加処理することからなっている。
That is, according to the method of the present invention, the polluted water generated when the concrete aggregate is washed is first treated with CMC and PMC.
AC treatment, and then cellulase is added to the supernatant obtained by coagulating and sedimenting the sludge.

【0011】[0011]

【発明の実施の形態】本発明は砕砂等を洗浄した際の汚
濁水を清澄化して再使用する際にコンクリートのスラン
プフローに影響のない良好な細骨材を得るための洗浄水
の再生方法でであるが、コンクリートプラントに於いて
日常発生するミキサーやアジテータ車等の洗浄水の回収
にも使用出来る方法であり、これによって処理された汚
濁水は再生水として、コンクリートの練り混ぜ水として
も十分使用できるものである。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention is a method for regenerating washing water to obtain good fine aggregate that does not affect the slump flow of concrete when clarifying and reusing polluted water obtained by washing crushed sand and the like. However, it is a method that can also be used to recover washing water from mixers and agitator trucks that are generated daily in concrete plants, and the contaminated water treated by this method is sufficient as reclaimed water and mixed water for concrete. It can be used.

【0012】本発明の第一段階で使用されるCMCは窯
業、石膏ボード関係で粘土鉱物質の分散剤、安定剤とし
て、また石油ボーリングの掘削泥水や建設工事の安定液
工法においてベントナイトスラリーを安定化させ、その
流動性を維持させるために広く使用されている。この様
にCMCは一般に水中で分散剤、安定化剤として使用さ
れており対象懸濁粒子が中性若しくは陰性に帯電してい
る場合には凝集剤としての効果はそれ自身には殆んど無
く、Ag,Cu,Pb,Zn,Al,Feなどのイオン
添加によってそのイオンに相当するCMCの不溶性金属
塩を形成して沈殿する性質を有している。
The CMC used in the first step of the present invention is used as a dispersant and a stabilizer for clay minerals in the fields of ceramics and gypsum board, and is used to stabilize bentonite slurry in drilling mud for oil drilling and in a stable liquid method for construction work. And is widely used to maintain its fluidity. As described above, CMC is generally used as a dispersant and a stabilizer in water, and when the target suspended particles are neutrally or negatively charged, the effect as a flocculant has almost no effect. , Ag, Cu, Pb, Zn, Al, Fe, etc., have the property of forming and precipitating an insoluble metal salt of CMC corresponding to the ion.

【0013】また、PACは正式には塩基性塩化アルミ
ニウムと称されるものであるが、一般に凝集剤として使
用されるものは4AlCl3 ・2Al(OH)3 ,3A
lCl3 ・3Al(OH)3 ,2ALCl3 ・4Al
(OH)3 ,AlCl3 ・5Al(OH)3 の混合物で
あり、商品としては低粘度でかつ凝集効果を高めるため
に若干の塩類などを添加されたものが通常用いられてい
る。このPACは水中では水和して水酸化アルミニウム
の高分子物となり強くプラスに帯電している。
PAC is formally referred to as basic aluminum chloride, but the one generally used as a flocculant is 4AlCl 3 .2Al (OH) 3 , 3A
lCl 3 .3Al (OH) 3 , 2ALCl 3 .4Al
It is a mixture of (OH) 3 , AlCl 3 .5Al (OH) 3 , and is generally used as a commercial product having a low viscosity and to which some salts or the like are added in order to enhance the coagulation effect. This PAC hydrates in water to become a polymer of aluminum hydroxide and is strongly positively charged.

【0014】本発明の第二段階で添加するセルラーゼは
セルロースを加水分解する酵素であり、最近では工業的
に生産され十分実用化される段階にきている。
The cellulase added in the second step of the present invention is an enzyme that hydrolyzes cellulose, and has recently reached the stage of industrial production and full practical use.

【0015】市販のセルラーゼから本発明に効果のある
セルラーゼを選択するには、CMCの1%水溶液を調製
し、この溶液に対し 0.5〜1.0ppmのセルラーゼを添加し
撹拌後静置してその溶液の粘度変化を測定する方法で可
能である。1%水溶液の粘度が500cps程度の場合、セル
ラーゼ添加3時間後で元の粘度の1/2 〜1/3 となり、一
日後で約1/10まで低下する。
In order to select a cellulase having an effect on the present invention from commercially available cellulases, a 1% aqueous solution of CMC is prepared, and 0.5 to 1.0 ppm of cellulase is added to the solution, and the solution is stirred and allowed to stand. It is possible by a method of measuring a change in viscosity of the liquid. When the viscosity of the 1% aqueous solution is about 500 cps, the viscosity becomes 1/2 to 1/3 of the original viscosity 3 hours after the addition of the cellulase, and decreases to about 1/10 after one day.

【0016】セルラーゼの種類や添加量は特に限定され
ないが、少量の添加で短時間で粘度低下効果の大きいも
のが好ましい。
The type and amount of the cellulase are not particularly limited, but those having a large effect of decreasing the viscosity in a short time by addition of a small amount are preferred.

【0017】本発明の第一段階において、砕砂等を洗浄
した際に発生する汚濁水にCMCを添加すると、CMC
が汚濁土粒子に吸着され保護コロイドを生成し、CMC
のアニオン性によって従来無機懸濁物質の持っていたマ
イナス荷電をより強くマイナスに帯電させる。次いでプ
ラス荷電を持っているPACを添加することによって電
荷が中和され、無機懸濁物質の持つ弱いマイナス荷電で
はとうてい沈殿しなかった無機微粒子まで急速に沈殿を
生成し、汚濁水を清澄化させることになる。
In the first step of the present invention, when CMC is added to polluted water generated when crushed sand or the like is washed, CMC is added.
Is absorbed by polluted soil particles to form protective colloid, and CMC
The negative charge of the inorganic suspension material is negatively charged more strongly by the anionic property of the inorganic suspension. Next, the charge is neutralized by adding a PAC having a positive charge, and a precipitate is rapidly formed to inorganic fine particles that were not precipitated by the weak negative charge of the inorganic suspended substance, thereby clarifying the polluted water. Will be.

【0018】この沈殿物を分離した後の回収水に凝集剤
として使用したCMCやPACが残存していると、ポリ
アクリルアミド系高分子凝集剤に較べるとはるかに弱い
がスランプフローに影響を与えるため、セルラーゼを添
加処理しCMCを分解することにより、コンクリートの
性状に影響を与えない洗浄細骨材を得ることが出来ると
いうものである。
If CMC or PAC used as a flocculant remains in the recovered water after separating this precipitate, the slump flow is affected, though much weaker than a polyacrylamide-based polymer flocculant. By adding cellulase and decomposing CMC, it is possible to obtain washed fine aggregate that does not affect the properties of concrete.

【0019】[0019]

【発明の効果】本発明の方法によって再生した洗浄水を
用いた細骨材を使用したコンクリートはポリアクリルア
ミド系高分子凝集剤を使用したものに較べてコンクリー
ト製造時のスランプフローへの影響が無く、良質なコン
クリートを提供することが出来る。
The concrete using fine aggregate using the washing water regenerated by the method of the present invention has no influence on the slump flow at the time of concrete production as compared with the one using a polyacrylamide polymer flocculant. It can provide high quality concrete.

【0020】[0020]

【実施例】次に実施例によって本発明をモルタル試験に
より、さらに詳細に説明する。
The present invention will now be described in more detail by way of examples with reference to a mortar test.

【0021】1)モルタル試験 1−1)モルタルの調製 JIS モルタルミキサに表1に示す配合により、使用細骨
材の1/2 量、セメント、細骨材の1/2 量、凝集剤等、A
E減水剤と水を順次添加し、5回撹拌羽根で混合した
後、180 秒間練り混ぜを行い調製した。
1) Mortar test 1-1) Preparation of mortar According to the composition shown in Table 1 in a JIS mortar mixer, 1/2 amount of fine aggregate used, セ メ ン ト amount of cement and fine aggregate, aggregating agent, etc. A
E The water reducing agent and water were sequentially added and mixed five times with a stirring blade, followed by kneading for 180 seconds to prepare.

【0022】[0022]

【表1】 [Table 1]

【0023】 1−2)使用材料 セメント :普通ポルトランドセメント(アサノ、三菱、秩父小野田セメント 社製品を等量混合、比重=3.16) 細骨材 :君津産陸砂(5mm on cut、比重=2.61、粗粒率=2.48) AE減水剤:リグニンスルホン酸系AE減水剤(商品名サンフローK、日本製 紙社製) 凝集剤 :ポリアクリルアミド系凝集剤(商品名コーナンフロックZH880H、 興南化学社製) ポリアクリルアミド系凝集剤(商品名コーヨーフロックP802、甲 陽ケミカル社製) 無機系凝集剤(商品名PAC#100L、浅田化学工業社製) CMC :商品名サンローズSN50C-P 、日本製紙社製 セルラーゼ:商品名セルラーゼA「アマノ」3、天野製薬社製 商品名セルソフトL、ノボノルディスクバイオインダストリー社 製1-2) Materials used Cement: Ordinary Portland cement (Asano, Mitsubishi, Chichibu Onoda Cement products are mixed in equal amounts, specific gravity = 3.16) Fine aggregate: Kimitsu land sand (5 mm on cut, specific gravity = 2.61, Coarse particle ratio = 2.48) AE water reducing agent: Lignin sulfonic acid type AE water reducing agent (trade name: Sanflow K, manufactured by Nippon Paper Co., Ltd.) Flocculant: polyacrylamide type flocculant (trade name: Konan Floc ZH880H, manufactured by Konan Chemical Co., Ltd.) Polyacrylamide-based flocculant (trade name: Koyo Floc P802, manufactured by Koyo Chemical Co., Ltd.) Inorganic flocculant (trade name: PAC # 100L, manufactured by Asada Chemical Industry Co., Ltd.) CMC: Sunrose SN50C-P, trade name; : Product name Cellulase A "Amano" 3, manufactured by Amano Pharmaceutical Company name Cellsoft L, manufactured by Novo Nordisk Bio-Industry

【0024】1−3)試験方法 モルタルのスランプはJIS A1101 に準じ、ミニスランプ
コーン(上端内径5cm,下端内径10cm,高さ15cmの鉄
製)により測定した。またその時のモルタルの広がりを
その直径を最大と認める方向とこれに直角な方向の2ヶ
所で測定し、スランプフローとした。また空気量はASTM
C185 に準じて測定した。
1-3) Test method The mortar slump was measured using a mini slump cone (iron having an upper inner diameter of 5 cm, a lower inner diameter of 10 cm, and a height of 15 cm) according to JIS A1101. Further, the spread of the mortar at that time was measured at two points, a direction in which the diameter was recognized as the maximum and a direction perpendicular to the direction, and the result was defined as a slump flow. The air volume is ASTM
It was measured according to C185.

【0025】なお、セルラーゼのCMC分解効果の判定
はCMC1%水溶液を調製し、セルラーゼを1.0ppm添加
した後の溶液粘度をB型回転粘度計で25.0℃で測定し
た。
The CMC decomposing effect of cellulase was determined by preparing a 1% aqueous solution of CMC, adding 1.0 ppm of cellulase, and measuring the solution viscosity at 25.0 ° C. using a B-type rotary viscometer.

【0026】2)試験結果 2−1)高分子凝集剤がスランプに及ぼす影響 表1に示す細骨材の1/2 とセメントをミキサに投入した
後、残りの細骨材にポリアクリルアミド系高分子凝集剤
を0.1%溶液で所定濃度添加混合した後、AE減水剤を溶
解した水を加えてモルタルを調製した。その結果を表2
の比較例2〜7に示す。ポリアクリルアミド系高分子凝
集剤は練り水に対して濃度10ppm からスランプ及びスラ
ンプフローに影響を与えることが分かる。
2) Test results 2-1) Influence of polymer flocculant on slump After half of the fine aggregate and cement shown in Table 1 were put into the mixer, the remaining fine aggregate was added to the polyacrylamide-based high aggregate. After a predetermined concentration of a molecular coagulant was added and mixed with a 0.1% solution, water in which an AE water reducing agent was dissolved was added to prepare a mortar. Table 2 shows the results.
Are shown in Comparative Examples 2 to 7. It can be seen that the polyacrylamide polymer flocculant affects slump and slump flow at a concentration of 10 ppm with respect to the kneading water.

【0027】2−2)PACがスランプに及ぼす影響 前項と同様にして、ポリアクリルアミド系高分子凝集剤
の代わりに、PACの1.0%溶液を所定濃度添加混合して
モルタルを調製した。その結果を表2の比較例8〜10に
示す。PACは練り水に対して濃度100 〜1,000ppmの添
加でもスランプにあまり影響しないことが分かる。
2-2) Effect of PAC on slump In the same manner as in the previous section, a 1.0% solution of PAC was added and mixed at a predetermined concentration in place of the polyacrylamide polymer flocculant to prepare a mortar. The results are shown in Comparative Examples 8 to 10 in Table 2. It can be seen that PAC does not significantly affect the slump even when it is added to the kneading water at a concentration of 100 to 1,000 ppm.

【0028】2−3)CMCがスランプに及ぼす影響 前項と同様にして、PACの代わりに、CMCの0.1%溶
液を所定濃度添加混合してモルタルを調製した。その結
果を表2の比較例11〜16に示す。CMCは練り水に対し
て濃度100ppm以上の添加からスランプ及びスランプフロ
ーに影響が出てくることが分かる。
2-3) Influence of CMC on slump In the same manner as in the previous section, a mortar was prepared by adding a 0.1% solution of CMC at a predetermined concentration and mixing instead of PAC. The results are shown in Comparative Examples 11 to 16 in Table 2. It can be seen that the addition of CMC to the kneading water at a concentration of 100 ppm or more affects slump and slump flow.

【0029】2−4)セルラーゼを添加したCMC・P
AC系がスランプに及ぼす影響 前項と同様に、CMCの0.1%溶液とPACの1.0%溶液の
所定濃度を混合し、1時間放置したものにセルラーゼを
1.0ppm添加混合してモルタルを調製した。その結
果を実施例1〜4に示す。本発明の洗浄水の回収方法に
よって得られた細骨材は凝集剤が付着してコンクリート
製造時に混入されたとしても、スランプ及びスランプフ
ローに影響を与えないことが分かる。
2-4) CMC · P containing cellulase
Influence of AC System on Slump As in the previous section, a mortar was prepared by mixing a predetermined concentration of a 0.1% solution of CMC and a 1.0% solution of PAC, adding 1.0 ppm of cellulase to a mixture left for 1 hour, and mixing. The results are shown in Examples 1 to 4. It can be seen that the fine aggregate obtained by the method for recovering washing water of the present invention does not affect the slump and the slump flow even if the flocculant adheres and is mixed during the production of concrete.

【0030】2−5)セルラーゼよるCMC溶液粘度の
変化 CMC1%水溶液に2種類のセルラーゼを1.0ppm添加
し、経時的に溶液粘度を測定した結果を表3に示す。何
れのセルラーゼも良くCMCを分解している。
2-5) Change in viscosity of CMC solution by cellulase Table 3 shows the results obtained by adding 1.0 ppm of two types of cellulase to a 1% aqueous solution of CMC and measuring the viscosity of the solution over time. All cellulases degrade CMC well.

【0031】[0031]

【表2】 [Table 2]

【0032】[0032]

【表3】 [Table 3]

───────────────────────────────────────────────────── フロントページの続き (72)発明者 工藤 正邦 埼玉県東松山市東平1551 日本製紙株式会 社コンクリート技術研究所内 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Masakuni Kudo 1551 Higashidaira, Higashimatsuyama-shi, Saitama Prefecture Nippon Paper Industries Co., Ltd.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 コンクリート用骨材を洗浄した際に発生
する汚濁水を再使用するにあたり、汚濁水をまずカルボ
キシメチルセルロースとポリ塩化アルミニウムで処理
し、次いでその上澄水にセルラーゼを添加して処理する
ことを特徴とするコンクリート用骨材洗浄水の再生方
法。
1. To reuse polluted water generated when washing aggregate for concrete, the polluted water is first treated with carboxymethylcellulose and polyaluminum chloride, and then treated by adding cellulase to the supernatant water. A method for regenerating aggregate washing water for concrete, comprising:
JP7629697A 1997-03-27 1997-03-27 Regeneration of cleaning water for aggregate for concrete Pending JPH10263313A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7629697A JPH10263313A (en) 1997-03-27 1997-03-27 Regeneration of cleaning water for aggregate for concrete

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7629697A JPH10263313A (en) 1997-03-27 1997-03-27 Regeneration of cleaning water for aggregate for concrete

Publications (1)

Publication Number Publication Date
JPH10263313A true JPH10263313A (en) 1998-10-06

Family

ID=13601404

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7629697A Pending JPH10263313A (en) 1997-03-27 1997-03-27 Regeneration of cleaning water for aggregate for concrete

Country Status (1)

Country Link
JP (1) JPH10263313A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006063467A1 (en) * 2004-12-17 2006-06-22 Iogen Energy Corporation Upflow settling reactor for enzymatic hydrolysis of cellulose
CN111875277A (en) * 2020-08-10 2020-11-03 中建四局土木工程有限公司 Sea sand desalting device and method
CN116462471A (en) * 2023-06-07 2023-07-21 成都理工大学 A kind of concrete prepared by using tunnel spoil and its preparation method

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006063467A1 (en) * 2004-12-17 2006-06-22 Iogen Energy Corporation Upflow settling reactor for enzymatic hydrolysis of cellulose
JP2008523788A (en) * 2004-12-17 2008-07-10 アイオゲン エナジー コーポレイション Upflow precipitation reactor for enzymatic hydrolysis of cellulose
US7727746B2 (en) 2004-12-17 2010-06-01 Iogen Energy Corporation Upflow reactor for enzymatic hydrolysis of cellulose
CN111875277A (en) * 2020-08-10 2020-11-03 中建四局土木工程有限公司 Sea sand desalting device and method
CN116462471A (en) * 2023-06-07 2023-07-21 成都理工大学 A kind of concrete prepared by using tunnel spoil and its preparation method
CN116462471B (en) * 2023-06-07 2025-03-14 成都理工大学 Concrete prepared from tunnel waste slag and preparation method thereof

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