JPS60202799A - Treatment of organic sludge - Google Patents

Treatment of organic sludge

Info

Publication number
JPS60202799A
JPS60202799A JP59054427A JP5442784A JPS60202799A JP S60202799 A JPS60202799 A JP S60202799A JP 59054427 A JP59054427 A JP 59054427A JP 5442784 A JP5442784 A JP 5442784A JP S60202799 A JPS60202799 A JP S60202799A
Authority
JP
Japan
Prior art keywords
air
drying
aeration
organic sludge
dried
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.)
Granted
Application number
JP59054427A
Other languages
Japanese (ja)
Other versions
JPH0311840B2 (en
Inventor
Katsuyuki Kataoka
克之 片岡
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.)
Ebara Corp
Original Assignee
Ebara Infilco 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 Ebara Infilco Co Ltd filed Critical Ebara Infilco Co Ltd
Priority to JP59054427A priority Critical patent/JPS60202799A/en
Publication of JPS60202799A publication Critical patent/JPS60202799A/en
Publication of JPH0311840B2 publication Critical patent/JPH0311840B2/ja
Granted legal-status Critical Current

Links

Classifications

    • 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
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Abstract

PURPOSE:To dry efficiently high water-content dehydrated cake by utilizing the heat retained by the discharged from an aeration blower for supplying air into an aeration vessel wherein organic sewage and sludge are treated, for the finish drying of the cake, and heating the discharged air which is utilized for the predrying of the cake. CONSTITUTION:The dehydrated cake 1 of organic sludge having about 70-80% water content is supplied into a predryer 2, for example, an agitation-granulation dryer, dried by the hot air 3 while being agitated and graulated, and converted into a granular predried material 4 having about 40-65% water content. The predried material 4 is subsequently supplied into a hermetic finish dryer 5 wherein a packed bed 6 is formed. The air 9 discharged from an aeration blower 8 fro supply aeration air into an aeration vessel 7 in the treating system of organic sewage, organic sludge, etc. is passed through said packed bed 6, and the predried material 4 forming the packed bed 6 is dried to obtain a material 10 having <40% water content (normally 20-30%).

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、下水、し尿、各種産業廃水などの有機性汚水
処理、有機性汚泥処理などにおいて発生する有機性汚泥
の脱水ケーキを、きわめて合理的かつ省エネルギ的に処
理する方法に関するものである。
[Detailed Description of the Invention] [Field of Industrial Application] The present invention provides an extremely rational method for dewatering cakes of organic sludge generated in the treatment of organic sewage such as sewage, human waste, and various industrial wastewater, and in the treatment of organic sludge. The present invention relates to a method for efficiently and energy-saving processing.

〔従来技術〕[Prior art]

有機性汚泥は、脱水−乾燥−焼却等で処分されるのが一
般的な方法であるが、脱、水で得られる脱水ケーキは含
水率70〜80襲程度であり、これを乾燥、焼却する際
に、 ■ 前記脱水ケーキの乾燥、焼却には多量の燃料を必要
とする。
Organic sludge is generally disposed of by dehydration, drying, and incineration, but the dehydrated cake obtained by dehydration has a moisture content of about 70 to 80%, and is then dried and incinerated. In this case, (1) Drying and incineration of the dehydrated cake requires a large amount of fuel.

■ 乾燥排ガスあるいは焼却排ガスの集じん及び脱臭処
理を必要とする。
■ Dust collection and deodorization treatment of dry exhaust gas or incineration exhaust gas is required.

といった問題点があり、特に焼却は乾燥の良否に左右さ
れるところから、乾燥を如何に効果的、合理的に行うか
がきわめて重要となっている。
Since incineration in particular depends on the quality of drying, it is extremely important to determine how effectively and rationally drying can be carried out.

〔発明の目的〕[Purpose of the invention]

本発明は、有機性汚泥の脱水ケーキの乾燥を予備乾燥と
仕上げ乾燥の2段に分割し、各乾燥を合理的に行い、前
記従来の問題点を解決する有機性汚泥の処理方法を提供
することを目的とするものである。
The present invention provides a method for treating organic sludge that divides the drying of a dehydrated cake of organic sludge into two stages, pre-drying and final drying, performs each drying process rationally, and solves the above-mentioned conventional problems. The purpose is to

〔発明の構成〕[Structure of the invention]

本発明は、有機性汚泥の脱水ケーキを、予備乾燥したの
ちさらに仕上げ乾燥するにあたり、有機性汚水、有機性
汚泥などの処理における味気槽に空気を供給する曝気プ
ロワの吐出空気の保有熱を前記仕上げ乾燥に利用し、該
仕上げ乾燥からの排空気を任意の熱源で加熱したのち前
記予備乾燥に利用し、さらに該予備乾燥からの排空気を
前記曝気槽に供給することを特徴とするものである。
In the present invention, when a dehydrated cake of organic sludge is pre-dried and then further dried, the retained heat of the discharged air of the aeration blower that supplies air to the taste tank in the treatment of organic sewage, organic sludge, etc. The exhaust air from the final drying is heated with an arbitrary heat source and then used for the preliminary drying, and the exhaust air from the preliminary drying is further supplied to the aeration tank. be.

〔実施例〕〔Example〕

本発明の一実施例を図面を参照しながら説明すれば、含
水率70〜80q6程度の有機性汚泥の脱水ケーキ1は
、予備乾燥器またとえば攪拌造粒乾燥機に供給され、攪
拌造粒されながら、後述する熱風3によって乾燥され、
含水率40〜65チ程度の粒状の予備乾燥物4に変換さ
れる。この予備乾燥物4は1次に密閉型の仕上げ乾燥器
5に供給されて充填層6を形成し、さらに充填層6内に
は、有機性汚水、有機性汚泥などの処理系内の曝気槽7
に曝気用の空気を供給する曝気プロワ8の吐出空気9を
通気し、この充填層6を形成する予備乾燥物4を含水率
40%未満(通常20〜60%程度)に乾燥し、乾燥物
10を得る。
An embodiment of the present invention will be described with reference to the drawings. A dehydrated cake 1 of organic sludge with a moisture content of about 70 to 80q6 is supplied to a pre-dryer or an agitation granulation dryer, and is agitated and granulated. While drying with hot air 3 described later,
It is converted into a granular pre-dried material 4 having a moisture content of about 40 to 65 inches. This pre-dried material 4 is first supplied to a closed finish dryer 5 to form a packed bed 6, and inside the packed bed 6 is an aeration tank for treating organic sewage, organic sludge, etc. 7
The discharge air 9 of the aeration blower 8 that supplies air for aeration is aerated, and the pre-dried material 4 forming the packed bed 6 is dried to a moisture content of less than 40% (usually about 20 to 60%). Get 10.

このように、仕上げ乾燥器5内の充填層乙に通気される
暖気プロワ8の吐出空気9の温度は、空気の断熱圧縮に
よって吸込み空気11の温度よりも上昇し、少なくとも
60〜70℃を示す。この結果、予備乾燥物中に含まれ
る少量の水分は、吐出空気9の前記保有熱量によって容
易に除去される。
In this way, the temperature of the discharge air 9 of the warm air blower 8 vented to the packed bed B in the finishing dryer 5 rises above the temperature of the suction air 11 due to the adiabatic compression of the air, and reaches at least 60 to 70°C. . As a result, a small amount of moisture contained in the pre-dried material is easily removed by the heat capacity of the discharged air 9.

しかして、仕上げ乾燥器5からの排空気12は、任意の
加熱源16によって加熱され、好ましくは300℃以上
の熱風6となって予備乾燥器2における脱水ケーキ1の
乾燥用熱源とする。予備乾燥器2から排出される排空気
14は、空気を主成分とするものであるから、これを曝
気槽7に送り、下水その他の有機性汚水15の生物処理
用の曝気用空気として利用する。
Thus, the exhaust air 12 from the finish dryer 5 is heated by an arbitrary heat source 16, preferably becomes hot air 6 of 300° C. or higher, and is used as a heat source for drying the dehydrated cake 1 in the pre-dryer 2. Since the exhaust air 14 discharged from the pre-dryer 2 is mainly composed of air, it is sent to the aeration tank 7 and used as aeration air for biological treatment of sewage and other organic wastewater 15. .

また、予備乾燥器5からの排空気14には、ダスト及び
臭気成分が含まれているが、曝気槽7の水中において集
じんされ、生物的に脱臭されるので、特別の集じん及び
脱臭装置は不要である。
Further, the exhaust air 14 from the pre-dryer 5 contains dust and odor components, but the dust is collected in the water in the aeration tank 7 and deodorized biologically, so a special dust collection and deodorization device is used. is not necessary.

なお、前記仕上げ乾燥器からの排空気12の加熱源16
としては、焼却設備16が付帯されているときは、乾燥
物10を焼却した燃焼排ガス、あるいは下水、し尿など
から回収した紙類などを含むし渣を焼却した焼却熱を利
用するのが好都合であり、加熱源16としての重油など
の有価燃料は不要となる。
Note that the heating source 16 of the exhaust air 12 from the finishing dryer
When the incineration equipment 16 is attached, it is convenient to use the combustion exhaust gas from incinerating the dry matter 10 or the incineration heat from incinerating the residue containing paper collected from sewage, human waste, etc. This eliminates the need for valuable fuel such as heavy oil as the heating source 16.

さらに、前記予備乾燥器2としては、供給された脱水ケ
ーキ1に、攪拌翼によって旋回流を与えながら熱風3を
下部から供給することによって。
Further, as the pre-dryer 2, the hot air 3 is supplied from the lower part to the supplied dehydrated cake 1 while giving a swirling flow using a stirring blade.

乾燥と造粒操作を同時に行うことができる造粒乾燥機を
使用するのが最も好適である。すなわち、造粒乾燥機か
ら排出される予備乾燥物4は、含水率が50〜60%程
度に適度に予備乾燥された粒径分布が狭い造粒物である
ため、仕上げ乾燥器5に供給したときに、非常に良好な
通気性をもつ充填層6を形成させることができ、充填層
厚を高くしても層下部の粒子が圧密されることがないと
いう重要なる効果があり、曝気プロワ8の吐出空気9の
もつ比較的少量の熱量をきわめて効率よく充填層6内に
おいて回収することができる。
It is most preferred to use a granulation dryer that can carry out drying and granulation operations simultaneously. That is, the pre-dried material 4 discharged from the granulation dryer is a granulated material with a narrow particle size distribution that has been suitably pre-dried to a moisture content of about 50 to 60%, so it was supplied to the finishing dryer 5. Sometimes, a packed bed 6 with very good air permeability can be formed, and even if the packed bed thickness is increased, the particles at the bottom of the layer will not be consolidated, which is an important effect. A relatively small amount of heat contained in the discharged air 9 can be recovered within the packed bed 6 very efficiently.

〔発明の効果〕〔Effect of the invention〕

以上述べたように本発明によれば、次のようなきわめて
重要なる効果を得ることができる。
As described above, according to the present invention, the following extremely important effects can be obtained.

■ 乾燥工程を2段に分割したので、含水率の高い脱水
ケーキに対しても合理的、省エネルギ的に乾燥すること
ができ、その後の焼却処理を有利にする。したがって、
下水やし尿などの生物処理工程から発生する難脱水性の
余剰活性汚泥に対しても効果的に適用することができる
- Since the drying process is divided into two stages, even a dehydrated cake with a high moisture content can be dried rationally and in an energy-saving manner, making subsequent incineration processing advantageous. therefore,
It can also be effectively applied to surplus activated sludge that is difficult to dewater and is generated from biological treatment processes such as sewage and human waste.

■ 脱水ケーキを、あらかじめ高温空気で予備的に乾燥
した予備乾燥物という特定物に対1−1比較的低温度の
暖気プロワ吐出空気の断熱圧縮熱によって仕上げ乾燥す
るというプロセス構成としたので、比較的熱容量として
は小さい暖気プロワ吐出空気の保有熱によっても、含水
率40チ未満の乾燥物を容易に得ることができる。
■ We used a process configuration in which the dehydrated cake is finished dried using the adiabatic compression heat of relatively low-temperature warm air blower discharge air against a specific material called pre-dried material, which has been pre-dried with high-temperature air. Even with the retained heat of the hot air blower discharge air, which has a small thermal capacity, it is possible to easily obtain a dried product with a moisture content of less than 40 inches.

すなわち、脱水ケーキを曝気ブロワの断熱圧縮熱のみに
よって乾燥しようとすると、脱水ケーキより乾燥除去す
べき水分の蒸発所要熱量に比べて、曝気ブロワの吐出空
気の保有熱量が著しく過少で、低水分にまで乾燥させる
ことはほとんど不可能であるが1本発明ではこのような
問題がない。
In other words, if you try to dry a dehydrated cake using only the heat of adiabatic compression from the aeration blower, the amount of heat retained in the air discharged from the aeration blower will be significantly less than the amount of heat required to evaporate the water that should be removed by drying from the dehydrated cake, resulting in a low moisture content. However, the present invention does not have this problem.

■ 乾燥排気の集じん及び脱臭を行うための特別の設備
が不要になる。
■ Special equipment for collecting dust and deodorizing dry exhaust air is no longer required.

■ 曝気槽に供給する空気は、高温熱風を使用する予備
乾燥から流出する排気であるから、その温度は冬期にお
いても60°C程度であり、曝気槽内の水温を低下させ
て生物処理への悪影響を及ぼすというトラブルがない。
■ The air supplied to the aeration tank is the exhaust air flowing out from pre-drying using high-temperature hot air, so its temperature is around 60°C even in winter, so it is possible to lower the water temperature in the aeration tank and use it for biological treatment. There are no problems with adverse effects.

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

図面は本発明の一実施例を示す系統説明図である。 j 1・・・脱水ケーキ、2・・・予備乾燥器、6・・
・熱風、4・・・予備乾燥物、5・・・仕上げ乾燥器、
6・・・充填層、7・・・曝気槽、8・・・曝気ブロワ
、9・・・吐出空気、10・・・乾燥物、11・・・吸
込み空気、12.14・・・排空気、16・・・加熱源
、15・・・有機性汚水、16・・焼却設備。 特許出願人 荏原インフィルコ株式会社代理人弁理士 
高 木 正 行
The drawing is a system explanatory diagram showing an embodiment of the present invention. j 1... Dehydrated cake, 2... Pre-dryer, 6...
・Hot air, 4... Pre-dried material, 5... Finishing dryer,
6... Filled bed, 7... Aeration tank, 8... Aeration blower, 9... Discharge air, 10... Dry material, 11... Suction air, 12.14... Exhaust air , 16...Heating source, 15...Organic sewage, 16...Incineration equipment. Patent applicant: Patent attorney representing Ebara Infilco Co., Ltd.
Masayuki Takagi

Claims (1)

【特許請求の範囲】 1、 有機性汚泥の脱水ケーキを、予備乾燥したのちさ
らに仕上げ乾燥するにあたり、有機性汚水、有機性汚泥
などの処理における曝気槽に空気を供給する曝気ブロワ
の吐出空気の保有熱を前記仕上げ乾燥に利用し、該仕上
げ乾燥からの排空気を任意の熱源で加熱したのち前記予
備乾燥に利用し、さらに該予備乾燥からの排空気を前記
曝気槽に供給することを特徴とする有機性汚泥の処理方
法。 2 前記予備乾燥を造粒乾燥たらしめ、該造粒乾燥物の
充填層を前記仕上げ乾燥時に形成させるものである特許
請求の範囲第1項記載の有機性汚泥の処理方法。
[Claims] 1. When pre-drying a dehydrated cake of organic sludge and then final drying it, the discharge air of an aeration blower that supplies air to an aeration tank in the treatment of organic sewage, organic sludge, etc. The retained heat is used for the final drying, the exhaust air from the final drying is heated with an arbitrary heat source and then used for the preliminary drying, and the exhaust air from the preliminary drying is further supplied to the aeration tank. A method for treating organic sludge. 2. The method for treating organic sludge according to claim 1, wherein the preliminary drying is granulated and dried, and a packed bed of the granulated dried product is formed during the final drying.
JP59054427A 1984-03-23 1984-03-23 Treatment of organic sludge Granted JPS60202799A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59054427A JPS60202799A (en) 1984-03-23 1984-03-23 Treatment of organic sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59054427A JPS60202799A (en) 1984-03-23 1984-03-23 Treatment of organic sludge

Publications (2)

Publication Number Publication Date
JPS60202799A true JPS60202799A (en) 1985-10-14
JPH0311840B2 JPH0311840B2 (en) 1991-02-18

Family

ID=12970416

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59054427A Granted JPS60202799A (en) 1984-03-23 1984-03-23 Treatment of organic sludge

Country Status (1)

Country Link
JP (1) JPS60202799A (en)

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5423188A (en) * 1977-07-22 1979-02-21 Eiken Chemical Culture medium for detecting acylamidase of bacteria
JPS596985A (en) * 1982-07-05 1984-01-14 Kubota Ltd Treatment of waste water with activated sludge
JPS5918372A (en) * 1982-07-23 1984-01-30 日本フア−ネス工業株式会社 Drying furnace for sludge

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5423188A (en) * 1977-07-22 1979-02-21 Eiken Chemical Culture medium for detecting acylamidase of bacteria
JPS596985A (en) * 1982-07-05 1984-01-14 Kubota Ltd Treatment of waste water with activated sludge
JPS5918372A (en) * 1982-07-23 1984-01-30 日本フア−ネス工業株式会社 Drying furnace for sludge

Also Published As

Publication number Publication date
JPH0311840B2 (en) 1991-02-18

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