JPH03169400A - Granulating and dewatering method of sludge - Google Patents

Granulating and dewatering method of sludge

Info

Publication number
JPH03169400A
JPH03169400A JP1311411A JP31141189A JPH03169400A JP H03169400 A JPH03169400 A JP H03169400A JP 1311411 A JP1311411 A JP 1311411A JP 31141189 A JP31141189 A JP 31141189A JP H03169400 A JPH03169400 A JP H03169400A
Authority
JP
Japan
Prior art keywords
sludge
collected
powder
cyclone
ash
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
JP1311411A
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 JP1311411A priority Critical patent/JPH03169400A/en
Publication of JPH03169400A publication Critical patent/JPH03169400A/en
Pending legal-status Critical Current

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  • Treatment Of Sludge (AREA)
  • Glanulating (AREA)

Abstract

PURPOSE:To lower sludge treatment cost and improve dewatering ratio by using incinerated ashes collected by a cyclone as they are or separated from rough particles or using incinerated ashes collected by electric precipitator and separated from fine powder or using both of them as drying powder. CONSTITUTION:A sludge cake primarily dewatered by a primary dehydrator 1 is supplied to a granulating machine 2. As drying powder, incinerated ashes discharged from an incinerator 4 and collected by a cyclone 5 are supplied to the granulating machine 2 as they are or separated from rough particles by screening using a screening machine 9, or incinerated ashes collected by an electric precipitator 6 and separated from fine powder by a screening machine 10 or both of them are supplied. The sludge cake is pulverized by the granulating machine 2 to a degree not to break the water route of the cake, granulated into granules by rotation, and the granules are coated with the drying powder. In this way, sludge treatment cost becomes low and dewatering ratio is heightened with a little amount of the drying powder and the sludge cake become easy to be handled.

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を、一次脱水した後
に脱水助剤として乾燥粉を被覆しっつ謂質汚泥粒に造粒
し、しかる後二次脱水する汚泥の遣粒脱水方法に関する
. 「従来の技術] 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
キを生成する技術としては、一次脱水した汚泥ケーキを
揺変(チキソトロビー変化〉を防ぎながら造粒して粒径
1〜10mmの汚泥粒となし、その際造粒しながら汚泥
粒の表面に珪藻土、消石灰、焼却灰等の乾燥粉を脱水助
材として被覆して調質汚泥粒となし、該調質汚泥粒を圧
搾して二次脱水して汚泥ケーキの含水率を60%以下に
する技術が、特公昭59−48160号公報に記載され
ている6 この方法の基本的な考え方は、汚泥ケーキを遣粒してこ
れを圧搾したときに含有水が速やがに汚泥粒表面まで到
達できるようにし、且つ乾燥粉の透水性が高いことを利
用して、汚泥粒に乾燥粉を被覆して汚泥粒表面まで到達
した含有水をろ材まで速やかに導く「水路Jの役目を果
たさせることにより、低含水率の汚泥ケーキを短時間に
容易に得ようとするものであった. 上記技術においては、乾燥粉の透水性を改善することに
より、調質汚泥粒を圧搾して二次脱水するときの含有水
の「はけ1を良くして、一層低含水率の汚泥ケーキの生
成を図ることが好ましい.このような乾燥粉の透水性を
改善する技術としては、乾燥粉中に乾重量比で1〜20
%の酸化アルミニウム又は水酸化アルミニウムを添加し
、あるいは焼却灰中にリンが0.5%以上残留するよう
焼却炉中にリン酸を噴露する技術が開発されている(特
願平1−5612号及び特願平1−21823号). 「発明が解決しようとする課題] 汚泥の脱水はその焼却・廃棄を目的とするものであるか
ら、所要コストの削減が強く求められている。しかるに
前記した従来技術では酸化アルミニウム、水酸化アルミ
ニウム、リン酸等の化学薬品に類するものを添加する必
要があり、しかも特に下水処理場で処理する一次脱水汚
泥ケーキの量は1日に数百トンにもなり、その結果添加
する化学薬品類が1日に数トンにもなる.したがって汚
泥の脱水のための所要コストが思うように下がらないと
いう問題点があった. 本発明は、上記した問題点を解消するために、乾燥粉の
透水性を低コストで改善し、且つ可能な限り閉サイクル
を形威した汚泥の造粒脱水方法を提供するものである. [課題を解決するための手段] 本発明者は上記課題を達或するために研究を重ね、乾燥
粉の透水性がその粒径に依存することを見出し、且つサ
イクロンで捕集した焼却灰と電気集塵機で捕集した焼却
灰とではその粒径が異なることを利用して、本発明を完
戒するに至った.すなわち本発明は、一次脱水した汚泥
ケーキと乾燥粉とを造粒機に僕給し、該造粒機において
前記乾燥粉を被覆した調質汚泥粒を形成し、該調質汚泥
粒を圧搾して二次脱水する汚泥の造粒脱水方法において
、前記二次脱水した汚泥ケーキを焼却炉によって焼却し
、該焼却炉より排出された焼却灰をサイクロンと電気集
塵機とによって捕集し、前記サイクロンにおいて捕集し
た焼却灰をそのまま若しくは粗粉を除去した後に前記乾
燥粉として用い、若しくは前記電気集塵機において捕集
した焼却灰より微粉を除去したものを前記乾燥粉として
用い、又はこれらの両者を前記乾燥粉として用いた汚泥
の造粒脱水方法である. [実施例1 本発明の実施例を図面を用いて説明する。第1図は本発
明の一実施例のフローシ一トであり、この実施例では先
ず汚泥は一次脱水機lによって一次脱水され、一次脱水
された汚泥ケーキは遣粒機2に供給される。遣粒機2に
は後記するように、焼却炉4から排出された後分級機9
.10にかけて分級した焼却灰も、同時に供給される。
Detailed Description of the Invention "Field of Industrial Application" The present invention involves firstly dewatering sludge generated in sewage systems, etc., and then granulating it into so-called solid sludge particles coated with dry powder as a dehydration aid. This relates to a method for dehydrating sludge through granulation, which is then subjected to secondary dewatering. ``Prior art'' As a technology for dewatering sludge generated in sewers, etc. to produce a sludge cake with a low moisture content, the sludge cake that has undergone primary dewatering is subjected to thixolysis. (Thixotrobi change) is granulated to form sludge particles with a particle size of 1 to 10 mm. During granulation, the surface of the sludge particles is coated with dry powder such as diatomaceous earth, slaked lime, or incinerated ash as a dewatering aid. A technique is described in Japanese Patent Publication No. 59-48160, in which the tempered sludge particles are compressed and subjected to secondary dehydration to reduce the moisture content of the sludge cake to 60% or less. The basic idea of the method is to allow the water contained in the sludge cake to quickly reach the surface of the sludge particles when it is compressed, and to take advantage of the high water permeability of the dry powder. By coating the sludge grains with dry powder to quickly guide the water that has reached the surface of the sludge grains to the filter media, it is possible to easily obtain a sludge cake with a low water content in a short time. In the above technology, by improving the water permeability of the dry powder, the drainage of the contained water during secondary dewatering by squeezing the conditioned sludge particles is improved, and It is preferable to produce a sludge cake with a low moisture content.As a technique for improving the water permeability of such dry powder, it is possible to
% of aluminum oxide or aluminum hydroxide, or spraying phosphoric acid into the incinerator so that 0.5% or more of phosphorus remains in the incinerated ash (Japanese Patent Application No. 1-5612) (No. 1 and Japanese Patent Application No. 1-21823). “Problems to be Solved by the Invention” Since the purpose of dewatering sludge is to incinerate and dispose of it, there is a strong need to reduce the required cost.However, in the prior art described above, aluminum oxide, aluminum hydroxide, It is necessary to add similar chemicals such as phosphoric acid, and in particular, the amount of primary dewatered sludge cake processed at sewage treatment plants is several hundred tons per day, and as a result, the amount of chemicals added is 1. This amounts to several tons per day.Therefore, there was a problem that the cost required for dewatering sludge did not go down as expected.In order to solve the above problems, the present invention improves the water permeability of dry powder. The object of the present invention is to provide a method for granulating and dewatering sludge that is improved at low cost and forms a closed cycle as much as possible. [Means for Solving the Problems] In order to achieve the above problems, the present inventors have Through repeated research, we discovered that the water permeability of dry powder depends on its particle size, and by taking advantage of the fact that the particle sizes of incinerated ash collected by a cyclone and incinerated ash collected by an electrostatic precipitator are different, The present invention has been completed.That is, the present invention involves feeding a primarily dehydrated sludge cake and dry powder to a granulator, and forming tempered sludge particles coated with the dry powder in the granulator. In the sludge granulation and dehydration method in which the tempered sludge particles are compressed for secondary dehydration, the sludge cake subjected to the secondary dewatering is incinerated in an incinerator, and the incinerated ash discharged from the incinerator is heated in a cyclone and electric The incinerated ash collected by the dust collector and the cyclone is used as the dry powder, or the incinerated ash collected by the electrostatic precipitator is used as the dry powder after removing the coarse powder, or the incinerated ash collected by the electrostatic precipitator is used as the dry powder. This is a method for granulating and dewatering sludge using the dry powder or both as the dry powder. [Example 1] An example of the present invention will be explained with reference to the drawings. Fig. 1 shows an example of the present invention. In this embodiment, sludge is first dehydrated by a primary dehydrator 1, and the primary dewatered sludge cake is supplied to a pelletizer 2.As will be described later, the pelletizer 2 includes: Classifier 9 after discharge from incinerator 4
.. Incineration ash that has been classified over 10 times is also supplied at the same time.

造粒機2において汚泥ケーキは、その中のキャビラリー
(水路)を破壊しない程度に破砕され、転勤によって粒
状に造粒され、且つ転動している間に汚泥粒表面に分級
した焼却灰が被覆されてゆく.造粒機2で造粒され且つ
分級した焼却灰で被覆した調質汚泥粒は、次の二次脱水
8!3に供給されて調質汚泥粒中の含有水が更に圧搾脱
水される.二次脱水113としてはより強力な圧搾力を
必要とするために、プレス式あるいは水圧ダイアフラム
式の圧搾脱水機が使用される6二次脱水を終えた汚泥ケ
ーキは焼却炉4に投入されて焼却される.焼却炉4は流
動層式焼却炉でもよいし,多段式焼却炉でもよいが、本
実際例では流動層式焼却炉を用いた。
In the granulator 2, the sludge cake is crushed to the extent that it does not destroy the cavities (channels) therein, and is granulated into granules by transfer, and while it is rolling, the classified incineration ash is deposited on the surface of the sludge particles. It is covered. The tempered sludge particles granulated by the granulator 2 and coated with classified incineration ash are supplied to the next secondary dehydration 8!3, where the water contained in the tempered sludge particles is further compressed and dehydrated. As secondary dewatering 113 requires stronger squeezing force, a press type or hydraulic diaphragm type press dehydrator is used. 6 After the secondary dewatering, the sludge cake is put into an incinerator 4 and incinerated. It will be done. The incinerator 4 may be a fluidized bed incinerator or a multistage incinerator, but in this practical example, a fluidized bed incinerator was used.

焼却された汚泥ケーキは燃焼ガスと焼却灰になるが、焼
却灰は燃焼ガスと共に流動してサイクロン5に送られ、
サイクロン5において燃焼ガス中の粗焼却灰が分離捕集
されて貯留ホッパ7゜に貯留される.燃焼ガスは次いで
電気集塵機6に導入され、ここで更に細焼却灰が分離捕
集されて貯留ホッパ8に貯留され、燃焼ガスは大気へ放
出される.貯留ホッパ7に貯留されたサイクロン捕集灰
と貯留ホッパ8に貯留された電気集塵機捕集灰とは、そ
れぞれ分級機9と分級機lOにかけて分級される.分級
I19.10は、本実施例では遠心力と空気抵抗とを利
用して分級する回転式分級機を使用した.分級機9によ
って粗粉を除去したサイクロン捕集灰と、分級機10に
よって微粉を除去した電気集塵機捕集灰とは、貯留ホッ
パ11に貯留された後,造粒機2へ供給される. 次に第1表は、分級機9によるサイクロン捕集灰の分級
結果(分級機回転数5000rpm)と、分級機10に
よる電気集塵機捕集灰の分級結果(同前)とを、サイク
ロン捕集灰と電気集塵機捕集灰とを分級しないで混合し
た場合の焼却灰と比較して示した表であり、焼却灰の粒
径はH e − N eレーザ光の照射によっておこる
回折リングの大きさによって計測した。同表における中
粉とは、粗粉又は微粉を除去した焼却灰であり、その粒
径の範囲は10〜80μmであった。
The incinerated sludge cake becomes combustion gas and incineration ash, but the incineration ash flows together with the combustion gas and is sent to cyclone 5.
Crude incineration ash in the combustion gas is separated and collected in cyclone 5 and stored in storage hopper 7°. The combustion gas is then introduced into the electrostatic precipitator 6, where fine incineration ash is further separated and collected and stored in the storage hopper 8, and the combustion gas is released into the atmosphere. The cyclone-collected ash stored in the storage hopper 7 and the electrostatic precipitator-collected ash stored in the storage hopper 8 are classified by a classifier 9 and a classifier 10, respectively. For classification I19.10, a rotary classifier that uses centrifugal force and air resistance for classification was used in this example. The cyclone-collected ash from which coarse powder has been removed by the classifier 9 and the electrostatic precipitator-collected ash from which fine powder has been removed by the classifier 10 are stored in a storage hopper 11 and then supplied to the granulator 2. Next, Table 1 shows the classification results of the cyclone-collected ash by the classifier 9 (classifier rotation speed 5000 rpm) and the classification results of the electrostatic precipitator-collected ash by the classifier 10 (same as above). This is a table showing a comparison between incinerated ash and ash collected by an electric precipitator without being classified. I measured it. The medium powder in the same table is incinerated ash from which coarse powder or fine powder has been removed, and its particle size range is 10 to 80 μm.

第1表 次に第2図は、分級しない場合と比較した本実施例の効
果を示した図である。図中「分級灰添加とは,本実施例
に従って分級機9によって粗粉を除去したサイクロン捕
集灰と、分級alioによって微粉を除去した電気集塵
機捕集灰とを脱水助剤として用いて二次脱水した場合を
示し、「無分級灰添加Jとは、サイクロン捕集灰と電気
集塵機捕集灰とを分級を行わないで脱水助剤として用い
て二次脱水した場合を示す.したがって「分級灰添加』
の焼却灰の平均粒径は、第■表より略22μm程度であ
り、「無分級灰添加jの平均粒径は11.6μmである
. また第2図縦軸の減水率とは、一次脱水した汚泥ケーキ
が含有している水分の量に対する、二次脱水によってし
ぼり出された水の量の割合である.本実験に使用した一
次脱水した汚泥ケーキの含水率は82%であった。また
横軸の灰添加率とは、一次脱水した汚泥ケーキの重量に
対する焼却灰の添加割合である. 第2図より明らかなように、平均粒径約22μm程度の
本実施例の方が、平均粒径11.6μmの無分級のとき
よりも、同一の減水率を得るために必要な灰添加率は多
くなっている。換言すれば、二次脱水によって所要の減
水率を得ようとするときには、微粒を除去した焼却灰を
脱水助剤として添加した方が、所要の灰量が少なくて済
むという′冫て・あA−庚添加誉がIレiけbげ ー〃
贈永得の汚泥ケーキの容積も少なくなり、焼却処分ある
いは埋立て等においての取扱いが容易になることは当然
である. なお焼却灰中の微粉が透水性を゛阻害する原因としては
、第1に、微粉になるほどその形状は球状に近くなって
「水路』を形戊し難くなること、第2に、粗粉同士が形
或した「水路Jに微粉が入り込んで「水路1を閉塞する
ことのためであると考えられる. 以上のように本実施例では、サイクロン捕集灰より粗粉
を除去し、電気集m機捕集灰より微粉を除去して脱水助
剤として用いたが、サイクロン捕集灰より粗粉を除去し
たものの平均粒径は23.2μmであり、電気集塵機捕
集灰より微粉を除去したものの平均粒径は21.6μm
であるから、これらのいずれかを単独で脱水助剤として
用いても、透水性の向上を図ることができる。また本実
施例においてサイクロン捕集灰より粗粉を除去した理由
は、焼却炉4内の珪砂などがサイクロン5に混入したと
きにこれを除去するためであって、■粉が透水性の向上
を阻害しているわけではない.したがってサイクロン捕
集灰をそのまま脱水助剤として用い,あるいはサイクロ
ン捕集灰と電気集塵機捕集灰より微粉を除去したものと
を脱水助剤として用いることもできる。
Table 1 and FIG. 2 are diagrams showing the effects of this example in comparison with the case without classification. In the figure, "classified ash addition" means that the cyclone-collected ash from which coarse powder has been removed by the classifier 9 according to this example and the electrostatic precipitator-collected ash from which fine powder has been removed by the classification alio are used as a dehydration aid to secondary ``Unclassified ash addition J'' refers to the case where cyclone-collected ash and electrostatic precipitator-collected ash are used as a dehydration aid without classification for secondary dehydration. Addition”
The average particle size of the incinerated ash is approximately 22 μm according to Table 1, and the average particle size of the unclassified ash added is 11.6 μm. This is the ratio of the amount of water squeezed out through secondary dehydration to the amount of water contained in the sludge cake.The water content of the sludge cake that was subjected to primary dewatering used in this experiment was 82%. The ash addition rate on the horizontal axis is the addition ratio of incinerated ash to the weight of the primary dehydrated sludge cake. The ash addition rate required to obtain the same water reduction rate is higher than when unclassified with a diameter of 11.6 μm.In other words, when trying to obtain the required water reduction rate by secondary dehydration, By adding incineration ash from which fine particles have been removed as a dehydration aid, the required amount of ash can be reduced.
It goes without saying that the volume of the sludge cake produced will be smaller, making it easier to handle when incinerated or landfilled. The reasons why fine powder in incinerated ash impedes water permeability are: first, the finer the powder, the more spherical it becomes, making it difficult to form a "water channel"; It is thought that this is because fine powder enters the waterway J and blocks the waterway 1.As described above, in this example, the coarse powder is removed from the cyclone-collected ash, and the electrolytic collection m Fine powder was removed from the ash collected by the machine and used as a dehydration aid, but the average particle size of the ash collected by the cyclone after removing the coarse powder was 23.2 μm, and the ash collected by the electrostatic precipitator after removing the fine powder was 23.2 μm. Average particle size is 21.6μm
Therefore, even if any one of these is used alone as a dehydration aid, water permeability can be improved. In addition, the reason why coarse powder was removed from the cyclone-collected ash in this example is to remove silica sand and the like from the incinerator 4 when it gets mixed into the cyclone 5. It's not a hindrance. Therefore, cyclone-collected ash can be used as it is as a dehydration aid, or cyclone-collected ash and electrostatic precipitator-collected ash from which fine powder has been removed can be used as a dehydration aid.

「発明の効果] 本発明は焼却灰の透水性がその粒径に依存することを利
用したものであるから、薬品類を脱水助剤として使用す
る場合に比して、汚泥の処理コストが小さくてすむ6ま
た無分級の焼却灰を脱水助剤として使用する場合に比し
て、少ない添加量で同等の減水率が得ることができ、し
たがって汚泥ケーキの取扱いが容易となる。
"Effects of the Invention" Since the present invention takes advantage of the fact that the water permeability of incinerated ash depends on its particle size, the cost of sludge treatment is lower than when chemicals are used as dewatering aids. In addition, compared to the case where unclassified incineration ash is used as a dehydration aid, the same water reduction rate can be obtained with a smaller amount added, and therefore the sludge cake is easier to handle.

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

第1図は本発明の一実施例のフローシ一トであり、第2
図は本発明と従来例とを比較した減水率を示す線図であ
る.
FIG. 1 is a flowchart of one embodiment of the present invention;
The figure is a diagram showing the water reduction rate comparing the present invention and the conventional example.

Claims (5)

【特許請求の範囲】[Claims] (1)一次脱水した汚泥ケーキと乾燥粉とを造粒機に供
給し、該造粒機において前記乾燥粉を被覆した調質汚泥
粒を形成し、該調質汚泥粒を圧搾して二次脱水する汚泥
の造粒脱水方法において、前記二次脱水した汚泥ケーキ
を焼却炉によって焼却し、該焼却炉より排出された焼却
灰をサイクロンと電気集塵機とによって捕集し、前記サ
イクロンにおいて捕集した焼却灰を前記乾燥粉として用
いたことを特徴とする汚泥の造粒脱水方法。
(1) The primary dewatered sludge cake and dry powder are supplied to a granulator, and the granulator forms tempered sludge particles coated with the dry powder, and the tempered sludge particles are compressed to form a secondary powder. In the granulation and dehydration method for sludge to be dehydrated, the secondary dewatered sludge cake is incinerated in an incinerator, the incinerated ash discharged from the incinerator is collected by a cyclone and an electrostatic precipitator, and the incineration ash is collected in the cyclone. A method for granulating and dewatering sludge, characterized in that incineration ash is used as the dry powder.
(2)前記サイクロンにおいて捕集した焼却灰より粗粉
を除去したものを前記乾燥粉として用いた請求項1記載
の汚泥の造粒脱水方法。
(2) The sludge granulation and dewatering method according to claim 1, wherein the dry powder is obtained by removing coarse powder from the incineration ash collected in the cyclone.
(3)前記電気集塵機において捕集した焼却灰より微粉
を除去したものを前記乾燥粉として用いた請求項1記載
の汚泥の造粒脱水方法。
(3) The sludge granulation and dewatering method according to claim 1, wherein the dried powder is obtained by removing fine powder from the incineration ash collected in the electrostatic precipitator.
(4)前記サイクロンにおいて捕集した焼却灰と、前記
電気集塵機において捕集した焼却灰より微粉を除去した
ものとを前記乾燥粉として用いた請求項1記載の汚泥の
造粒脱水方法。
(4) The sludge granulation and dewatering method according to claim 1, wherein the incinerated ash collected in the cyclone and the incinerated ash collected in the electrostatic precipitator after removing fine powder are used as the dry powder.
(5)前記サイクロンにおいて捕集した焼却灰より粗粉
を除去したものと、前記電気集塵機において捕集した焼
却灰より微粉を除去したものとを前記乾燥粉として用い
た請求項1記載の汚泥の造粒脱水方法。
(5) The sludge according to claim 1, wherein coarse powder is removed from the incinerated ash collected in the cyclone and fine powder is removed from the incinerated ash collected in the electrostatic precipitator as the dry powder. Granulation dehydration method.
JP1311411A 1989-11-29 1989-11-29 Granulating and dewatering method of sludge Pending JPH03169400A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1311411A JPH03169400A (en) 1989-11-29 1989-11-29 Granulating and dewatering method of sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1311411A JPH03169400A (en) 1989-11-29 1989-11-29 Granulating and dewatering method of sludge

Publications (1)

Publication Number Publication Date
JPH03169400A true JPH03169400A (en) 1991-07-23

Family

ID=18016883

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1311411A Pending JPH03169400A (en) 1989-11-29 1989-11-29 Granulating and dewatering method of sludge

Country Status (1)

Country Link
JP (1) JPH03169400A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH06109205A (en) * 1992-09-24 1994-04-19 Hitachi Zosen Corp Method of recovering heat from waste gas produced during baking in sludge resource activation system
KR20000003205A (en) * 1998-06-26 2000-01-15 이해규 Waste melting process device
CN102964053A (en) * 2012-11-09 2013-03-13 徐渊 Domestic sludge drying treatment method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH06109205A (en) * 1992-09-24 1994-04-19 Hitachi Zosen Corp Method of recovering heat from waste gas produced during baking in sludge resource activation system
KR20000003205A (en) * 1998-06-26 2000-01-15 이해규 Waste melting process device
CN102964053A (en) * 2012-11-09 2013-03-13 徐渊 Domestic sludge drying treatment method

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