JPS5834420B2 - Koukasei Soseibutsu - Google Patents
Koukasei SoseibutsuInfo
- Publication number
- JPS5834420B2 JPS5834420B2 JP50041986A JP4198675A JPS5834420B2 JP S5834420 B2 JPS5834420 B2 JP S5834420B2 JP 50041986 A JP50041986 A JP 50041986A JP 4198675 A JP4198675 A JP 4198675A JP S5834420 B2 JPS5834420 B2 JP S5834420B2
- Authority
- JP
- Japan
- Prior art keywords
- bentonite
- water
- ash
- construction
- waste
- 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
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P40/00—Technologies relating to the processing of minerals
- Y02P40/10—Production of cement, e.g. improving or optimising the production methods; Cement grinding
Landscapes
- Treatment Of Sludge (AREA)
- Curing Cements, Concrete, And Artificial Stone (AREA)
Description
【発明の詳細な説明】
この発明は、大量に発生し、しかも処理がきわめて困難
な建設用ベントナイト廃泥水と下水汚泥の焼成灰とを、
きわめて簡単な処理によって有効利用を図ることを目的
とした建設用ベントナイト廃泥水の処理方法に関するも
のである。DETAILED DESCRIPTION OF THE INVENTION The present invention uses construction bentonite waste mud water and sewage sludge burnt ash, which are generated in large quantities and are extremely difficult to treat.
This invention relates to a method for treating construction bentonite waste water, which aims to utilize it effectively through extremely simple treatment.
従来、建設施工にあたって、ベントナイト泥水を用いる
各種の特殊工法(たとえば、ベット、リバースサーキュ
レーション、連続壁、泥水シールド等の方法)を採用す
ると、大量のベントナイト廃泥水が排出される。BACKGROUND ART Conventionally, when various special construction methods using bentonite mud (for example, methods such as beds, reverse circulation, continuous walls, and mud shields) are employed during construction, a large amount of waste bentonite mud is discharged.
このベントナイト廃泥水は、最初の施工時においては含
水率85〜95%程度のベントナイトのコロイド分散系
の液であり、これに分散剤(たとえばリグニンスルホン
酸ナトリウム等)および増粘剤(たとえばカルボキシメ
チルセルロースCMC等)を含み、比重が約1.05〜
1.20程度のものであるが、施工終了後においては、
現地盤と接するため、砂礫、シルト、粘土等が混入し、
また接触地盤から各種金属陽イオンが、さらにはセメン
ト材料等も混入して、液を再循環させればさせるほど、
液組成は複雑になって、ゲル化現象を呈し、水分と固形
分との分離はきわめて困難なものとなる。This bentonite waste mud water is a colloidal dispersion of bentonite with a water content of about 85 to 95% at the time of initial construction, and is mixed with a dispersant (e.g., sodium ligninsulfonate) and a thickener (e.g., carboxymethyl cellulose). CMC, etc.) and has a specific gravity of approximately 1.05~
It is about 1.20, but after the construction is completed,
Because it comes into contact with the local ground, gravel, silt, clay, etc. are mixed in.
In addition, various metal cations and even cement materials are mixed in from the contact ground, and the more the liquid is recirculated, the more
The liquid composition becomes complex and exhibits a gelation phenomenon, making separation of water and solid content extremely difficult.
したがって、このような廃泥水の処理は固液分離が不可
能であるため、多量の水で希釈し、水処理的に、凝集沈
澱、濾過、脱水等の操作をするといったきわめて複雑な
処理を行なわざるを得なくなり、その処理費は美大なも
のとなり、かつ、分離された固形物の用途はなく、適当
な廃棄場所も少ないので、施工業者は廃泥水の処理に困
惑しているのが現状である。Therefore, since solid-liquid separation is not possible in the treatment of such waste mudwater, it is necessary to dilute it with a large amount of water and perform extremely complicated water treatment operations such as coagulation and sedimentation, filtration, and dewatering. Currently, construction companies are at a loss as to how to dispose of waste muddy water, as the treatment costs are prohibitive, and there is no use for the separated solids, and there are few suitable disposal sites. It is.
一方、下水処理場から大量に生ずる下水汚泥を焼却して
得られる焼成灰も、適当な用途も廃棄場所もないためも
当事者はこれく処分に苦慮している。On the other hand, those involved are having difficulty disposing of the ash obtained by incinerating the large amounts of sewage sludge produced at sewage treatment plants, as there is no suitable use for it or a place to dispose of it.
したがって、この発明はこのような現状に着目してなさ
れたものであり、含水率70%以上の建設用ベントナイ
ト廃泥水に、セメント類を添加するかまたは添加しない
で、吸水性の大きい下水汚泥の焼成灰を添加混合するこ
とを特徴とする建設用廃泥水の処理方法を提供するもの
である。Therefore, the present invention has been made with attention to the current situation, and aims to convert sewage sludge with high water absorption into waste bentonite slurry for construction with a moisture content of 70% or more, with or without adding cement. The present invention provides a method for treating construction waste water characterized by adding and mixing burnt ash.
以下にその詳細を述べる。The details are described below.
この発明における建設用ベントナイト廃泥水(以下廃泥
水と略称する)とは、砂礫、シルト、粘土、各種金属イ
オン、セメント材料、分散剤、増粘剤等の1種または2
種以上が混在しているきわめて複雑な組成のもので、通
常水分が70%以上で、ベントナイトを含む固液分離の
きわめて困難な泥水であり、下水汚泥の焼成灰(以下焼
成灰と略称する)は、下水汚泥を通常1000℃以上で
焼成して得られる空隙率70φ以上、真比重2.98、
吸水率80%程度の粉粒状物質であって、吸水率のきわ
めて高いものである。In this invention, the bentonite waste mud water for construction (hereinafter abbreviated as waste mud water) refers to one or two of the following: sand and gravel, silt, clay, various metal ions, cement materials, dispersants, thickeners, etc.
It is a muddy water with an extremely complex composition in which more than one species coexist, usually has a water content of 70% or more, and contains bentonite, making solid-liquid separation extremely difficult. is obtained by firing sewage sludge at a temperature of usually 1000°C or higher, with a porosity of 70φ or higher and a true specific gravity of 2.98.
It is a powdery substance with a water absorption rate of about 80%, and has an extremely high water absorption rate.
したがって、廃泥水と焼成灰とを混合すれば、廃泥水中
の水分が焼成灰に吸収されると同時に、廃泥水中の固形
分は焼成灰と固相反応を起し、養生することによって固
化する。Therefore, if waste mud water and fired ash are mixed, the moisture in the waste mud water is absorbed by the fired ash, and at the same time, the solid content in the waste mud water causes a solid phase reaction with the fired ash, and solidifies by curing. do.
この発明は固液分離のきわめて困難な廃泥水と、加水し
ただけでは固化しない焼成灰とを単に混合養生させるの
みで硬化性組成物が得られるので、両者がそれぞれ有す
る欠点を同時に解消するものであり、得られる硬化性組
成物はフィルセメント化材もしくはその原料、または、
低強度注入モルタルの原料として有用であるので、処理
方法が簡単であるということばかりではなく、得られる
組成物の有用性をも考え合わすならば、この発明の効果
がいかに大きいものであるかは明らかである。In this invention, a curable composition can be obtained by simply mixing and curing waste mud water, which is extremely difficult to separate from solid-liquid, and fired ash, which does not solidify even by adding water, thereby simultaneously solving the drawbacks of both. The curable composition obtained is a fill cementing material or its raw material, or
Since it is useful as a raw material for low-strength injection mortar, the effects of this invention are significant, considering not only the simple processing method but also the usefulness of the resulting composition. it is obvious.
ここにいうフィルセメント化材とはつき固めて7日間湿
潤養生した場合の圧縮強度が2h/−以上のものをいう
。The term "fill cement material" as used herein refers to a material that has a compressive strength of 2 h/- or more when compacted and cured in wet conditions for 7 days.
低強度注入モルタルとは、20℃における粘度が400
0〜5000cps、原料を混合し3時間経過後のブリ
ージング率が5%以下であり、養生日数に応じ圧縮強度
が増加するもので、28日後の圧縮強度が2−5#/c
疏哄上のものをいう。Low-strength injection mortar has a viscosity of 400 at 20°C.
0 to 5000 cps, the breathing rate after 3 hours after mixing the raw materials is 5% or less, and the compressive strength increases depending on the number of days of curing, and the compressive strength after 28 days is 2-5#/c
Refers to something that is on a song.
この発明の方法によって得られる硬化性組成物から低強
度注入モルタルを得るには、ベントナイト含量の多少に
応じ焼成灰の混合量を加減して適量のセメントを混合す
ればよい。In order to obtain a low-strength injection mortar from the curable composition obtained by the method of the present invention, it is sufficient to mix an appropriate amount of cement by adjusting the amount of calcined ash mixed depending on the bentonite content.
たとえば、ベントナイト含量20〜50 ky/m’の
廃泥水1m3当り焼成灰400〜280Ayとセメント
200kf混合すればよい。For example, 400 to 280 Ay of calcined ash and 200 kf of cement may be mixed per 1 m3 of waste mud water having a bentonite content of 20 to 50 ky/m'.
またフィルセメント化するには水分/(焼成灰+ベント
ナイト)の値が約0.75程度になるように焼成灰の混
合量を加減すればよい。Further, in order to form fill cement, the amount of mixed burned ash may be adjusted so that the value of moisture/(burned ash + bentonite) is about 0.75.
強度の大なものを欲するならばセメント、生石灰または
焼石膏の如き水硬性素材を配合すればよい。If high strength is desired, a hydraulic material such as cement, quicklime or calcined gypsum may be added.
したがって、この発明における廃泥水と焼成灰との混合
割合とともに、水硬性素材の添加量を適宜調整すれば、
任意の性状を示す硬化組成物を得ることができる。Therefore, if the mixing ratio of waste mud water and fired ash in this invention and the amount of hydraulic material added are adjusted appropriately,
Cured compositions exhibiting arbitrary properties can be obtained.
実施列 1
ベントナイト含量43.5ky/m3のベントナイト液
廃水1(lに焼成灰3.8に9およびセメント2kgを
混合して低強度注入モルタルを得た。Example 1 A low-strength pouring mortar was obtained by mixing 1 l of bentonite liquid wastewater with a bentonite content of 43.5 ky/m3, 3.8 l of calcined ash, and 2 kg of cement.
この物性はつぎのとおりであった。The physical properties were as follows.
すなわち、20℃における粘度 4500 c
ps3時間後のプリージング率 0.63 多圧縮
強度は第1表のとおりである。That is, the viscosity at 20°C is 4500 c
ps Pleasing rate after 3 hours 0.63 Multi-compression strength is as shown in Table 1.
第 1 表
湿潤養生日数 圧縮強度ky/cd72.2
14 4.328
7、556
10.7実施列 2
ベントナイト含量42ky/m3のベントナイト廃泥水
1(lに焼成灰13i’に混合してフィルセメント化材
を得た。Table 1 Moist curing days Compressive strength ky/cd 72.2 14 4.328
7,556
10.7 Example 2 1 (l) of bentonite waste slurry having a bentonite content of 42 ky/m3 was mixed with 13 i' of burned ash to obtain a fill cement material.
これを湿潤養生したものの圧縮強度は第2表のとおりで
ある。The compressive strength of this sample after wet curing is shown in Table 2.
第 2 表
湿潤養生日数 圧縮強度ky/crti32.5
73.0
14 3.328
3.756
4・9実施例 3
ベントナイト含量44h/rn’のベントナイト廃泥水
10tに焼成灰12に9と七メン)0.6#を混合して
ソイルセメント化材を得た。Table 2 Wet curing days Compressive strength ky/crti32.5 73.0 14 3.328
3.756
4.9 Example 3 A soil cementing material was obtained by mixing 10 tons of bentonite waste mud with a bentonite content of 44 h/rn', 12 tons of burned ash, 9 and 0.6 # of calcined ash.
これを湿潤養生したものの圧縮強度は第3表のとおりで
ある。The compressive strength of this sample after wet curing is shown in Table 3.
第 3 表
湿潤養生日数 圧縮強度kf/c12
13.0
7 16.5Table 3 Wet curing days Compressive strength kf/c12
13.0 7 16.5
Claims (1)
添加混合することを特徴とする建設用ベントナイト廃泥
水の処理方法。 2 建設用ベントナイト廃泥水に、セメント類とともに
下水汚泥の焼成灰を添加混合することを特徴とする建設
用ベントナイト廃泥水の処理方法。[Scope of Claims] 1. A method for treating construction bentonite waste water, which comprises adding and mixing burnt ash of sewage sludge to construction bentonite waste water. 2. A method for treating construction bentonite waste water, which comprises adding and mixing together cement and burned ash of sewage sludge with construction bentonite waste water.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP50041986A JPS5834420B2 (en) | 1975-04-04 | 1975-04-04 | Koukasei Soseibutsu |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP50041986A JPS5834420B2 (en) | 1975-04-04 | 1975-04-04 | Koukasei Soseibutsu |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS51116824A JPS51116824A (en) | 1976-10-14 |
| JPS5834420B2 true JPS5834420B2 (en) | 1983-07-26 |
Family
ID=12623509
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP50041986A Expired JPS5834420B2 (en) | 1975-04-04 | 1975-04-04 | Koukasei Soseibutsu |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5834420B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4886115B2 (en) * | 2000-04-13 | 2012-02-29 | 東京都下水道サービス株式会社 | Cement milk |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE2232084B2 (en) * | 1972-06-30 | 1980-10-16 | Bayer Ag, 5090 Leverkusen | Powder coating agents |
| JPS5117504B2 (en) * | 1972-09-06 | 1976-06-02 |
-
1975
- 1975-04-04 JP JP50041986A patent/JPS5834420B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS51116824A (en) | 1976-10-14 |
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