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JPH03288598A - Method for granulating and dehydrating sludge - Google Patents

Method for granulating and dehydrating sludge

Info

Publication number
JPH03288598A
JPH03288598A JP2089702A JP8970290A JPH03288598A JP H03288598 A JPH03288598 A JP H03288598A JP 2089702 A JP2089702 A JP 2089702A JP 8970290 A JP8970290 A JP 8970290A JP H03288598 A JPH03288598 A JP H03288598A
Authority
JP
Japan
Prior art keywords
sludge
particles
incineration ash
dehydration
heat
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
JP2089702A
Other languages
Japanese (ja)
Inventor
Tatsuo Kato
龍夫 加藤
Shusuke Narutomi
成富 修輔
Kazuo Endo
遠藤 和夫
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.)
Proterial Ltd
Original Assignee
Hitachi Metals 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 Hitachi Metals Ltd filed Critical Hitachi Metals Ltd
Priority to JP2089702A priority Critical patent/JPH03288598A/en
Publication of JPH03288598A publication Critical patent/JPH03288598A/en
Pending legal-status Critical Current

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  • Treatment Of Sludge (AREA)

Abstract

PURPOSE:To increase the coefficient of water permeability of incineration ash and to improve dehydration effect by heat-treating a dry powder at 800-1200 deg.C to coat the surfaces of the sludge particles from a sludge cake subjected to primary dehydration with the heat-treated powder and subjecting the obtained conditioned sludge particles to secondary dehydration. CONSTITUTION:A sludge cake subjected to primary dehydration is granulated to form sludge particles and the surfaces of these sludge particles are coated with a dry powder heat-treated at 800-1200 deg.C to prepare conditioned sludge which is, in turn, subjected to secondary dehydration. When incineration ash is heated at 800-1200 deg.C, the fine particles in the incineration ash are fused to be formed into coarse particles and the coarse particles becomes particles increased in unevenness as a whole. These coarse particles have a large specific surface area and, therefore, the capillary suction force thereof, that is, the force drawing out water from sludge particles thereof becomes strong and the secondary dehydration effect thereof becomes large. Further, the yield of incineration ash can be secured different from classification and the replenishment from the outside can be excluded.

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は、下水道等で発生する汚泥の処理方法に係るも
のであり、特に汚泥を脱水して汚泥ケーキとなし、これ
を焼却処理する方法に関する。
[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to a method for treating sludge generated in sewerage systems, etc., and particularly a method for dewatering sludge to form a sludge cake and incinerating it. Regarding.

[従来の技術] 従来より、下水道等で発生する汚泥を脱水して、低含水
率の汚泥ケーキにするには、一次脱水した汚泥ケーキを
更に二次脱水することが行なわれている。例えば、雑誌
「再生と利用J 1981.VoL−4に開示しである
如くである。しかしそれは一次脱水した汚泥ケーキをそ
のままの状態で二次脱水するものであり、それのみでは
十分な脱水効果を得ることができなかった。そこでこの
改善方法として、特公昭59−48160号公報に開示
しであるように、次脱水した汚泥ケーキに脱水助剤しと
て、主として焼却灰、他に珪藻土、消石灰、炭酸カルシ
ウム、微粉炭等の透水性の大きい乾燥粉を、汚泥ケーキ
の乾重量の10〜100%添加して、揺動変化を防ぎな
がら汚泥粒を形成し、汚泥粒の表面を前記した乾燥粉で
被覆して調質汚泥粒とし、これを加圧圧搾して汚泥ケー
キの含水率を50%以下にするというものであった。
[Prior Art] Conventionally, in order to dehydrate sludge generated in sewers and the like to obtain a sludge cake with a low water content, a sludge cake that has been primarily dehydrated has been subjected to secondary dewatering. For example, it is disclosed in the magazine "Recycling and Utilization J 1981. VoL-4. However, in this method, the sludge cake that has undergone primary dewatering is subjected to secondary dehydration as it is, and this alone does not provide sufficient dehydration effect. Therefore, as a method for improving this, as disclosed in Japanese Patent Publication No. 59-48160, a dewatering aid is applied to the dewatered sludge cake, and mainly incinerated ash, diatomaceous earth, and slaked lime are added to the sludge cake. Dry powder with high water permeability such as calcium carbonate, pulverized coal, etc. is added in an amount of 10 to 100% of the dry weight of the sludge cake to form sludge particles while preventing fluctuation changes, and the surface of the sludge particles is dried as described above. The sludge was coated with powder to form tempered sludge particles, which were then compressed and compressed to reduce the moisture content of the sludge cake to 50% or less.

[@明が解決しようとする問題点コ しかし上記した汚泥の造粒脱水方法においては、焼却灰
等の成分を未調整の状態で用いて脚質汚泥粒を作り、こ
れを二次脱水しているが、発明者らのその後の実験の結
果、次のような問題点があることが判明した。
[Problems that Akira is trying to solve] However, in the sludge granulation and dewatering method described above, components such as incineration ash are used in an unadjusted state to create leggy sludge particles, which are then subjected to secondary dehydration. However, as a result of subsequent experiments by the inventors, the following problems were found.

焼却灰には粗粒と細粒とが混在しており、これをそのま
まの状態で汚泥粒に被覆して二次脱水するのに比し、焼
却灰を分級して細粒を除去したものを被覆して二次脱水
した方が脱水効果が大きいことが判明した。しかし、焼
却灰を分級して細粒を除去し粗粒のみを使用する場合、
その収量バランスがくずれて量不足になることがしばし
ば起こるという問題点があった。
Incineration ash contains a mixture of coarse particles and fine particles, and compared to coating sludge grains with this as-is and performing secondary dehydration, incineration ash is classified and fine particles are removed. It was found that coating and secondary dehydration had a greater dehydration effect. However, when incineration ash is classified to remove fine particles and use only coarse particles,
There has been a problem in that the yield balance is disrupted and there is often a shortage of quantity.

本発明は上記欠点を解消した汚泥の造粒脱水方法を提供
することを目的とする。
An object of the present invention is to provide a method for granulating and dewatering sludge that eliminates the above-mentioned drawbacks.

[問題点を解決するための手段] 本発明は、一次脱水した汚泥ケーキを造粒して汚泥粒を
形成し、汚泥粒の表面に乾燥粉を被覆して調質汚泥粒と
なし、これを二次脱水する汚泥の造粒脱水方法において
、乾燥粉を800〜1200℃に加熱処理し、しかる後
に汚泥粒の表面に被覆したことを特徴とするものである
[Means for Solving the Problems] The present invention involves granulating a sludge cake that has undergone primary dewatering to form sludge particles, coating the surface of the sludge particles with dry powder to form tempered sludge particles, and This method of granulating and dewatering sludge for secondary dewatering is characterized in that dry powder is heat treated at 800 to 1200°C and then coated on the surface of sludge particles.

焼却灰を800〜1200℃の温度範囲で加熱すると、
焼却灰中の細粒が粗粒に融着して、粗粒全体が凹凸の大
きい粒となる。このような粗粒は比表面積が大きく、従
って毛細管吸引力つまりは汚泥粒より水を引き出す力が
強くなり、二次脱水効果が大きくなるのである。
When incinerated ash is heated in the temperature range of 800-1200℃,
The fine particles in the incineration ash fuse with the coarse particles, and the entire coarse particles become grains with large irregularities. Such coarse particles have a large specific surface area, and therefore have a strong capillary suction force, that is, a force to draw out water from the sludge particles, and the secondary dewatering effect becomes large.

[実施例] 本発明の詳細な説明する。[Example] The present invention will be described in detail.

第1図は焼却灰を900℃、1000℃、1100’C
の各温度に加熱処理したものを汚泥粒に被覆して二次脱
水したときの焼却灰の添加率と減水率との関係を示した
線図である。第2図は焼却灰の加熱温度と透水係数との
関係を示した線図である。
Figure 1 shows incineration ash at 900℃, 1000℃, and 1100'C.
It is a diagram showing the relationship between the addition rate of incinerated ash and the water reduction rate when sludge grains are coated with sludge particles heat-treated to various temperatures and subjected to secondary dehydration. FIG. 2 is a diagram showing the relationship between the heating temperature of incinerated ash and the hydraulic conductivity.

そして焼却灰を加熱したときの、加熱温度と焼却灰の性
状を第1表に示す。
Table 1 shows the heating temperature and properties of the incinerated ash when the incinerated ash was heated.

第1表 加熱温度(’C)平均粒径(−)   球形度(−)原
  粉     8.8   10.2Xlo−”90
0    9.5   9.61XIO−”1000 
  12.6   8.42xtO−”1100   
15.3   8.30XlO−”第1表によれば加熱
温度が高くなるにつれ、焼却灰の平均粒径が大きくなり
球形度は小さくなる。
Table 1 Heating temperature ('C) Average particle size (-) Sphericity (-) Raw powder 8.8 10.2Xlo-"90
0 9.5 9.61XIO-”1000
12.6 8.42xtO-”1100
15.3 8.30

これは加熱温度が高くなるほど、粗粒に付着する細粒の
量が多くなり、がっ粗粒の凹凸が大きくなったことを示
している。このように加熱処理した焼却灰を使用して調
質汚泥粒を作り、二次脱水した結果が第1図に示す線図
である。第1図における焼却灰添加率とは、一次脱水ケ
ーキの乾重量に対する焼却灰の添加重量の比である。焼
却灰の添加率を同一にした場合、焼却灰の加熱温度が高
いほど減水率が大きくなり、脱水効果が大きくなったも
のと判断できる。次に第2図によれば、焼却灰の加熱温
度を高くするほど透水係数が太きくなっている。透水係
数が大きいということは、焼却灰中を水が通り易くなっ
ていることを示し、第1図に示した結果を裏付けるもの
である。
This indicates that as the heating temperature increases, the amount of fine particles adhering to the coarse particles increases, and the unevenness of the coarse particles becomes larger. The heat-treated incineration ash was used to prepare tempered sludge grains, and the results of secondary dehydration are shown in the diagram shown in FIG. The incineration ash addition rate in FIG. 1 is the ratio of the added weight of incineration ash to the dry weight of the primary dehydrated cake. When the addition rate of incinerated ash is the same, the higher the heating temperature of incinerated ash, the greater the water reduction rate, and it can be judged that the dehydration effect becomes greater. Next, according to FIG. 2, the higher the heating temperature of the incinerated ash, the greater the hydraulic conductivity coefficient. A large hydraulic conductivity indicates that water can easily pass through the incinerated ash, which supports the results shown in Figure 1.

なお、今回実施した焼却灰では1200℃以上に加熱す
ると溶融して固形化してしまい、脱水助剤としての役目
を果たさなくなり、またs o o ’c以下では爆着
がおこらず、加熱の意味が無かった。
The incineration ash used this time will melt and solidify if heated above 1,200°C, and will no longer serve as a dehydration aid. Also, if the incineration ash is heated to 1,200°C or higher, no explosion will occur, meaning that heating is meaningless. There wasn't.

[発明の効果] 本発明は、焼却灰を加熱してその中の細粒を粗粒に融着
させて、凹凸の大きい焼却灰としたので、焼却灰の透水
係数を大きくでき、ひいては脱水効果を大きくすること
ができ、しかも分級と相違して焼却灰の収量を確保でき
て外部からの補給を排除することができる。
[Effects of the Invention] The present invention heats the incinerated ash and fuses the fine particles therein to the coarse particles to produce incinerated ash with large irregularities, so the permeability coefficient of the incinerated ash can be increased, and the dehydration effect can be increased. Moreover, unlike classification, the yield of incinerated ash can be secured and supply from outside can be eliminated.

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

Claims (1)

【特許請求の範囲】 1)一次脱水した汚泥ケーキを造粒して汚泥粒を形成し
、汚泥粒の表面に乾燥粉を被覆して調質汚泥粒となし、
これを二次脱水する汚泥の造粒脱水方法において、 乾燥粉を800〜1200℃に加熱処理し、しかる後に
汚泥粒の表面に被覆したことを特徴とする汚泥の造粒脱
水方法。 2)乾燥粉は焼却灰であることを特徴とする特許請求の
範囲第1項記載の汚泥の造粒脱水方法。
[Scope of Claims] 1) granulating a sludge cake that has undergone primary dewatering to form sludge particles, and coating the surface of the sludge particles with dry powder to form tempered sludge particles;
A method for granulating and dewatering sludge in which the sludge is subjected to secondary dewatering, characterized in that the dried powder is heat-treated at 800 to 1200°C and then coated on the surface of the sludge particles. 2) The sludge granulation and dewatering method according to claim 1, wherein the dry powder is incineration ash.
JP2089702A 1990-04-04 1990-04-04 Method for granulating and dehydrating sludge Pending JPH03288598A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2089702A JPH03288598A (en) 1990-04-04 1990-04-04 Method for granulating and dehydrating sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2089702A JPH03288598A (en) 1990-04-04 1990-04-04 Method for granulating and dehydrating sludge

Publications (1)

Publication Number Publication Date
JPH03288598A true JPH03288598A (en) 1991-12-18

Family

ID=13978111

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2089702A Pending JPH03288598A (en) 1990-04-04 1990-04-04 Method for granulating and dehydrating sludge

Country Status (1)

Country Link
JP (1) JPH03288598A (en)

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