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JPS6045960B2 - Consolidation material for sludge - Google Patents
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JPS6045960B2 - Consolidation material for sludge - Google Patents

Consolidation material for sludge

Info

Publication number
JPS6045960B2
JPS6045960B2 JP51041720A JP4172076A JPS6045960B2 JP S6045960 B2 JPS6045960 B2 JP S6045960B2 JP 51041720 A JP51041720 A JP 51041720A JP 4172076 A JP4172076 A JP 4172076A JP S6045960 B2 JPS6045960 B2 JP S6045960B2
Authority
JP
Japan
Prior art keywords
sludge
weight
quicklime
amount
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
Application number
JP51041720A
Other languages
Japanese (ja)
Other versions
JPS52124753A (en
Inventor
晃次 中川
昭三 酒巻
四郎 松永
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.)
Denka Co Ltd
Original Assignee
Denki Kagaku Kogyo 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 Denki Kagaku Kogyo KK filed Critical Denki Kagaku Kogyo KK
Priority to JP51041720A priority Critical patent/JPS6045960B2/en
Publication of JPS52124753A publication Critical patent/JPS52124753A/en
Publication of JPS6045960B2 publication Critical patent/JPS6045960B2/en
Expired legal-status Critical Current

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  • Treatment Of Sludge (AREA)

Description

【発明の詳細な説明】 本発明は汚泥用固結材に関するものである。[Detailed description of the invention] The present invention relates to a consolidation material for sludge.

河川の底に沈澱した汚泥、重金属類を含む産業廃棄物
汚泥、浄水場、下水処理場の汚泥または水分を含んた粘
土からなる汚泥等は、しばしば人体に有害な成分を含有
したり、臭気を発生することかあるため、その適切有効
な処理法が強く要望されている。 たとえは浄水処理場
における汚泥処理問題について説明すると、従来の供給
原水の水質は良好で含有する浮遊物質の濃度が極めて低
かつたため、そこから発生する汚泥は、河川への再循環
方式等によつて処理して来たが最近に至り、原水中の浮
遊物質の濃度が高くなり、これによる汚泥量の増加も著
しくなつてくると同時に、これを再び河川に希釈放流す
ることについてもいろいろな制約を受けるようになつた
Sludge that has settled on the bottom of rivers, industrial waste sludge containing heavy metals, sludge from water treatment plants and sewage treatment plants, and sludge made of moist clay often contain components that are harmful to the human body or emit odors. Since this may occur, there is a strong need for an appropriate and effective treatment method. For example, to explain the problem of sludge treatment at a water treatment plant, the quality of the raw water supplied in the past was good and the concentration of suspended solids contained was extremely low. However, recently, the concentration of suspended solids in raw water has increased, and the amount of sludge due to this has increased significantly.At the same time, there are various restrictions on diluting and discharging this sludge back into rivers. I started receiving it.

ことに重金属などの有害物質を含む産業廃棄物において
は一段と厳しい要求がある。 従来よりこれらの汚泥を
処理する方法としては、汚泥を脱水しケーキ状に固めて
投棄する方法やセメント、生石灰などの水硬性材料で固
結する方法などが提案されているが、前者の方法は投棄
場所の制限を受けると共に雨などによつて再び流出する
のを防止する処置が必要である。
In particular, there are even more stringent requirements for industrial waste containing hazardous substances such as heavy metals. Conventionally, methods of treating this sludge have been proposed, such as dewatering the sludge, solidifying it into a cake shape, and dumping it, or solidifying it with hydraulic materials such as cement or quicklime. In addition to restricting dumping locations, measures must be taken to prevent the waste from flowing out again due to rain.

一方、後者の方法によるとこのような欠点を取り除くこ
とができるが、一般に汚泥は大量の水の中に例えば粘土
などの微細な粒子や有機物を含んでいるので、セメント
や生石灰の水和による硬化が進み難い上に、硬化したも
のの固さも低いため、これを所要強度に硬化させるため
には、あるいはさらにこれを埋立、土木建築の材料とし
で使用するためには、大量のセメント、生石灰を汚泥に
混合しなければいけないという欠点があつた。 これら
の欠点を解決する目的で、カルシウムアルミネート系鉱
物と無機硫酸塩の特定割合からなる混合物をセメントに
配合してなる固結材が提案されているが(特開昭50−
133167号公報)、それとて未だ十分であるとはい
えない。
On the other hand, the latter method can eliminate these drawbacks, but sludge generally contains fine particles such as clay and organic matter in a large amount of water, so sludge cannot be hardened by hydration of cement or quicklime. It is difficult to proceed, and the hardness of the hardened material is low, so in order to harden it to the required strength, or to use it as a material for landfill or civil engineering construction, large amounts of cement and quicklime must be mixed with sludge. The disadvantage was that it had to be mixed with In order to solve these drawbacks, a setting material made by blending cement with a mixture of calcium aluminate minerals and inorganic sulfates has been proposed (Japanese Patent Application Laid-Open No. 1983-1999).
133167), but it still cannot be said to be sufficient.

本発明者は汚泥に少量分散混合するぁけで強固な硬化
体にできる固結材について種々研究した結果、3Ca0
−3A1.03・CaSO4又は3Ca03A1203
・CaF2,生石灰及び硫酸カルシウムを含有する水硬
性組成物がこの目的に卓越した効果があることを知見し
本発明を完成したものである。
As a result of various studies on caking materials that can be made into a strong hardened body by dispersing and mixing a small amount in sludge, the present inventor found that 3Ca0
-3A1.03・CaSO4 or 3Ca03A1203
- The present invention was completed after discovering that a hydraulic composition containing CaF2, quicklime, and calcium sulfate has an outstanding effect for this purpose.

以下詳しく本発明を説明する。本発明において3Ca0
−3A1203・CaSO4はアウインと称されている
鉱物であり、天然産ならびに合成品の別なく使用できる
。硫酸カルシウムとしては、無水石膏、半水石膏及び二
水石膏の各種の硫酸カルシウムが使用てきるが、好まし
くは無水石膏である。その他硫酸ナトリウムの使用も可
能である。この中のある組合せのものは一般にセメント
膨張材として用いられているもので、水和してエトリン
ジヤイトが生成するとされているものであり、具体的に
は商品名のデンカCSAやアサノジプカルなどがある。
The present invention will be explained in detail below. In the present invention, 3Ca0
-3A1203.CaSO4 is a mineral called Auin, and can be used regardless of whether it is a natural product or a synthetic product. As the calcium sulfate, various calcium sulfates such as anhydrite, hemihydrate, and dihydrate can be used, but anhydrite is preferable. It is also possible to use sodium sulfate. Among these, certain combinations are generally used as cement expansion agents and are said to produce ettringite when hydrated, and specific examples include the trade names Denka CSA and Asano dypcal.

こられ3成分の好ましい割合は、アウインが3〜印重量
%特に好ましくは10〜40重量%,生石灰が5〜35
重量%特に好ましくは10〜(イ)重量%および硫酸カ
ルシウムが30〜7睡量%特に好ましくは40〜6鍾量
%である。これらの組成になる固結材を得るにはこれら
の各成分をあらかじめ製造しておいて一定量混合する方
法やAl2O3源、CaO源およびSO3源の原料をほ
ぼ目的とする組成になるように調合し、1200〜14
00゜C程度の温度て焼成する方法がある。またアウイ
ンの代りに3Ca0−3A1203・CaF2なる化合
物を用いても、アウインを用いた場合とほぼ同等の効果
がある。粉末度には制約を受けず、プレーン値で200
0cd1y程度もあれば十分である。本発明の固結材は
、前記特開昭50−133167号公報に記載されたも
のに比べて、エトリンジヤイトを多量かつ短時間に生成
するのて汚泥の処理能率が向上する。
The preferred proportions of these three components are 3 to 40% by weight of Auin, particularly preferably 10 to 40% by weight, and 5 to 35% by weight of quicklime.
Particularly preferably 10 to (i) weight % and calcium sulfate 30 to 7 weight %, particularly preferably 40 to 6 weight %. In order to obtain a consolidation material with these compositions, it is necessary to prepare each of these components in advance and mix them in a certain amount, or to mix the raw materials for the Al2O3 source, CaO source, and SO3 source so that they have approximately the desired composition. 1200~14
There is a method of firing at a temperature of about 00°C. Furthermore, even if a compound called 3Ca0-3A1203.CaF2 is used instead of Auin, the effect is almost the same as when Auin is used. No restrictions on fineness, plain value 200
Approximately 0 cd1y is sufficient. The caking material of the present invention produces ettringite in a large amount and in a short period of time, thereby improving sludge treatment efficiency, compared to that described in JP-A-50-133167.

その理由は、生石灰はセメントに比べて、短時間にかつ
多大な発熱を伴なつて表面積の大きな(水和活性の大き
な)消石灰を生成するので、アウイン、硫酸カルシウム
との反応を著しく高めるからである。本発明固結材を用
いるにおいては、汚泥に混合分散するだけで十分であり
、その方法は特別な手段を必要とすることなく、通常の
バッチ混合法、連続混合のいずれをも自由に選択するこ
とがきる。
The reason for this is that compared to cement, quicklime produces slaked lime with a large surface area (high hydration activity) in a short time and with a large amount of heat generation, which significantly increases the reaction with auin and calcium sulfate. be. When using the caking material of the present invention, it is sufficient to mix and disperse it into sludge, and the method can be freely selected from either the normal batch mixing method or continuous mixing without requiring any special means. I can do things.

次に本発明固結材の使用量について説明する。Next, the usage amount of the consolidation material of the present invention will be explained.

一般に固化処理を必要とする汚泥には汚泥含水比WIS
(W:水、S:固型分を示す)が5踵量%以上であり、
しばしば10呼量%以上のものがほとんどである。これ
を固化するために必要な本発明固結材の量はほとんど汚
泥中に含まれている水量と密接な関係にあるので、水量
に基いて、かつ固化したものの利用ならびに処理に必要
な強度発現を考えて必要量添加する。具体的には汚泥中
の水に対してあまりにも少ない使用量では全く固化の目
的を達成きないので、通常は汚泥中の水量に対して5重
量%以上使用する。またその水量が5唾量%以下の汚泥
に対してもその固化を促進させるために用いることが望
ましいことである。本発明によると、少ない使用量で汚
泥を固結できしかもその強度も大きいという効果があり
、また重金属を含む汚泥を固化したものについては固化
後の重金属の流出が非常に少なくなるという利点がある
。以下実施例により本発明を説明する。
Sludge water content ratio WIS is generally used for sludge that requires solidification treatment.
(W: water, S: solid content) is 5% or more in heel weight,
Often, the amount is more than 10%. The amount of the sludge of the present invention required to solidify the sludge is closely related to the amount of water contained in the sludge. Consider and add the required amount. Specifically, if the amount used is too small relative to the water in the sludge, the purpose of solidification will not be achieved at all, so it is usually used in an amount of 5% by weight or more relative to the amount of water in the sludge. Furthermore, it is desirable to use it for promoting the solidification of sludge whose water content is 5% or less. According to the present invention, it is possible to solidify sludge with a small amount of use, and its strength is also high.Also, in the case of solidified sludge containing heavy metals, there is an advantage that the outflow of heavy metals after solidification is extremely small. . The present invention will be explained below with reference to Examples.

実施例1 浄水場で採取したWISが200重量%の汚泥に、電気
化学工業(株)製商品名デンカCSA#20(アウjイ
ン)15.9重量%,生石灰17.鍾量%および無水石
膏48.踵量%含有)を十分混合分散せしめて内径16
cm1深さ15びの容器に流し込み、これを20℃の恒
温室に水が蒸発しないようにしておき、各材令における
強度発現をASTMC4O3−65Tに規定さ・れたプ
ロクター貫入抵抗法に準じて測定した。
Example 1 Sludge containing 200% by weight of WIS collected at a water treatment plant was added with 15.9% by weight of Denka CSA #20 (trade name) manufactured by Denki Kagaku Kogyo Co., Ltd. and 17% by weight of quicklime. Lime weight % and anhydrite 48. (containing % heel weight) was sufficiently mixed and dispersed to obtain an inner diameter of 16
The material was poured into a container with a depth of 15 cm and kept in a thermostatic chamber at 20°C to prevent water from evaporating, and the strength development at each age was determined according to the Proctor penetration resistance method specified in ASTM C4O3-65T. It was measured.

その結果ならびに配合条件を第1表に示す。実施例2 実施例1の方法においてWISが10唾量%の汚泥につ
いて同じく強度発現を測定した結果を第2表に示す。
The results and blending conditions are shown in Table 1. Example 2 Table 2 shows the results of measuring the strength development of sludge with WIS of 10% saliva using the method of Example 1.

ただしこの場合CAS#20を混合分散した汚泥は団子
状になつてしまうので、5層に分けて1層につき30回
の割合で断面4×4cmの突き棒でつきながら内径16
cm,深さ15c7nの所定の容器の中につめた。実施
例3 実施例1においてCAS#20の代りに日本セメント(
株)製商品名アサノジプカル(アウイン4.9重量%,
生石灰33.1重量%および無水石膏46.4重量%含
有)を使用した結果を第3表に示す。
However, in this case, the sludge mixed and dispersed with CAS#20 will become lump-like, so divide it into 5 layers and pound with a ram with a cross section of 4 x 4 cm 30 times per layer.
It was packed in a predetermined container with a depth of 15 cm and a depth of 15 cm. Example 3 In Example 1, Nippon Cement (
Co., Ltd. product name: Asanojipcal (auin 4.9% by weight,
Table 3 shows the results using 33.1% by weight of quicklime and 46.4% by weight of anhydrite.

比較例1 実施例1においてデンカCAS#20の代りにボルトラ
ンドセメント及び生石灰をExpNO.lの割合で汚泥
に混合分散せしめた結果を第4表に示す。
Comparative Example 1 In Example 1, Exp NO. Table 4 shows the results of mixing and dispersing in sludge at a ratio of 1.

実施例4次に実施例1の汚泥の代りに、砕石をつくる際
の砕石水洪水に含まれる土砂を沈澱池で堆積した中で、
最も微粒な部分を採取した汚泥について行つた結果を第
5表に示す。
Example 4 Next, instead of the sludge in Example 1, earth and sand contained in the crushed stone water flood used when making crushed stone was deposited in a settling tank.
Table 5 shows the results for the sludge from which the finest particles were collected.

実施例5 電気炉で溶融焼成して得られた 3Ca0●3A1203●CaF2クリンカーをプレー
ン値4.500cイlダに粉砕したもの1重量部、5T
!$L下生石灰1重量部及び無水石膏2重量部を配合し
て固結材を調整した。
Example 5 3Ca0●3A1203●CaF2 clinker obtained by melting and firing in an electric furnace was ground to a plain value of 4.500 ml, 1 part by weight, 5T
! A consolidation material was prepared by blending 1 part by weight of $L quicklime and 2 parts by weight of anhydrite.

これをWISl5O重量%の汚泥に対して1呼量%添加
し混合したところ、3紛て固化し1日の圧縮強度は2k
gIcT1てあつた。
When this was added at 1 volume% to WISl5O weight% sludge and mixed, 3 pieces solidified and the compressive strength in 1 day was 2K.
gIcT1 was prepared.

比較のため、この固結材において、生石灰1重量部のか
わりに普通ボルトランドセメント7重量部を配合してな
る固結材を用いて同様な固化処理を行なつたが、1日た
つても固化はしなかつた。
For comparison, a similar solidification process was carried out using a solidification material containing 7 parts by weight of ordinary Boltland cement instead of 1 part by weight of quicklime, but even after one day, It did not solidify.

なお、固結材の水和物をX線回折によつて測定ノしたと
ころ、いずれもエトリンジヤイトの生成が認められた。
次に、その後、引き続き所定材令まで放置して圧縮強度
を測定した結果を第6表に示す。
In addition, when the hydrates of the consolidation materials were measured by X-ray diffraction, the formation of ettringite was observed in all cases.
Next, Table 6 shows the results of measuring the compressive strength after allowing the specimen to stand until a predetermined material age.

本発明例ては、材令の経過にともなつて強度増進した。In the examples of the present invention, the strength increased as the material aged.

Claims (1)

【特許請求の範囲】[Claims] 1 3CaO・3Al_2O_3・CaSO_4又は3
CaO・3Al_2O_3・CaF_23〜50重量%
、生石灰5〜35重量%及び硫酸カルシウム30〜70
重量%を含有してなる汚泥用固結材。
1 3CaO・3Al_2O_3・CaSO_4 or 3
CaO・3Al_2O_3・CaF_23-50% by weight
, quicklime 5-35% by weight and calcium sulfate 30-70%
A solidification material for sludge containing % by weight.
JP51041720A 1976-04-13 1976-04-13 Consolidation material for sludge Expired JPS6045960B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP51041720A JPS6045960B2 (en) 1976-04-13 1976-04-13 Consolidation material for sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP51041720A JPS6045960B2 (en) 1976-04-13 1976-04-13 Consolidation material for sludge

Publications (2)

Publication Number Publication Date
JPS52124753A JPS52124753A (en) 1977-10-20
JPS6045960B2 true JPS6045960B2 (en) 1985-10-12

Family

ID=12616248

Family Applications (1)

Application Number Title Priority Date Filing Date
JP51041720A Expired JPS6045960B2 (en) 1976-04-13 1976-04-13 Consolidation material for sludge

Country Status (1)

Country Link
JP (1) JPS6045960B2 (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5518210A (en) * 1978-07-24 1980-02-08 Nippon Cement Co Ltd Sludge solidification treating agent
JPS60156600A (en) * 1984-01-26 1985-08-16 Asahi Chem Ind Co Ltd Dehydration and solidification of water-containing sludge
JPS6265799A (en) * 1985-09-18 1987-03-25 Tokyo Giken Kogyo Kk Flocculating, adsorbing, dehydrating and solidifying agent for sludge in waste water
JP2013007599A (en) * 2011-06-23 2013-01-10 Denki Kagaku Kogyo Kk Solidification material for contaminated water and processing method
JP5909133B2 (en) * 2012-03-29 2016-04-26 太平洋マテリアル株式会社 Treatment method for radioactive contaminants
JP5909132B2 (en) * 2012-03-29 2016-04-26 太平洋マテリアル株式会社 Treatment method for radioactive contaminants

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5713359B2 (en) * 1974-04-10 1982-03-16

Also Published As

Publication number Publication date
JPS52124753A (en) 1977-10-20

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