JPH0985299A - Method for decreasing quantity of organic sludge - Google Patents

Method for decreasing quantity of organic sludge

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Publication number
JPH0985299A
JPH0985299A JP24470095A JP24470095A JPH0985299A JP H0985299 A JPH0985299 A JP H0985299A JP 24470095 A JP24470095 A JP 24470095A JP 24470095 A JP24470095 A JP 24470095A JP H0985299 A JPH0985299 A JP H0985299A
Authority
JP
Japan
Prior art keywords
sludge
digested
anaerobic digestion
ozone
solid
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
JP24470095A
Other languages
Japanese (ja)
Other versions
JP3447027B2 (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 Corp
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 Corp filed Critical Ebara Corp
Priority to JP24470095A priority Critical patent/JP3447027B2/en
Publication of JPH0985299A publication Critical patent/JPH0985299A/en
Application granted granted Critical
Publication of JP3447027B2 publication Critical patent/JP3447027B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Treatment Of Sludge (AREA)

Abstract

PROBLEM TO BE SOLVED: To effectively and economically decrease the quantity of org. sludge by anaerobically digesting org. sludge in an anaerobic digestion process and adding ozone or hydrogen peroxide to the digested sludge to solubilize the sludge and further anaerobically digesting the solubilized sludge. SOLUTION: Org. sludge 1 such as sewage raw sludge or excessive activated sludge is anaerobically digested in an anaerobic digestion process 2 at first and a part easily decomposable biologically is decreased in quantity. About 60wt.% of SS of raw sludge is digested herein. The remaining digested sludge is drawn out to a chemical oxidizing process 3 and ozone or hydrogen peroxide is added to the sludge to solubilize the same. Next, the solubilized sludge is further anaerobically digested by anaerobic bacteria in a second anaerobic digestion process 4 to be decomposed to carbon dioxide and water. By this method, 90wt.% or more of raw sludge can be decreased in quantity. The digested sludge of the second anaerobic digestion process 4 is subjected to solid-liquid separation and the separated soln. 5 is drained and the solid is treated as sludge residue 6.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、下水生汚泥、余剰
活性汚泥、混合生汚泥などの有機性汚泥を大幅に減量化
する方法に関する。
TECHNICAL FIELD The present invention relates to a method for significantly reducing the amount of organic sludge such as sewage raw sludge, surplus activated sludge, and mixed raw sludge.

【0002】[0002]

【従来の技術】下水の活性汚泥処理施設などからは下水
汚泥、余剰活性汚泥や生汚泥などの有機性汚泥(以下、
「原汚泥」ということもある)が大量に発生しており、
それらの発生量は下水道の施設の拡充に伴って増大しつ
つあり、現在その増大する有機性汚泥の処理処分が最大
の問題となっている。従来、有機性汚泥は脱水助剤(有
機高分子ポリマーなど)を添加し、脱水機で脱水された
後、焼却処分されているが、汚泥が大量の場合には、脱
水機及び焼却炉が大規模なものになり、設備費、維持管
理費などが多大の額となり、焼却処分は経済的にも困難
のものとなっている。
2. Description of the Related Art Organic sludge such as sewage sludge, excess activated sludge and raw sludge (hereinafter,
A lot of "raw sludge" is generated,
The amount of those generated is increasing with the expansion of sewerage facilities, and the treatment and disposal of the increasing organic sludge is now the biggest problem. Conventionally, organic sludge has been dehydrated with a dehydration aid (organic polymer, etc.) and then incinerated after being dehydrated. However, if a large amount of sludge is used, the dehydrator and incinerator are large. It becomes a large scale, the equipment cost, the maintenance cost, etc. are large, and the incineration becomes economically difficult.

【0003】この問題を解決する手段の1つとして、有
機性汚泥の減量化があり、それには種々の手段が提案さ
れている。汚泥の減量化の手段の1つとして従来より生
物学的な汚泥減量化方法があり、それには嫌気性消化法
や好気性消化法が知られている。しかし、それら生物学
的な汚泥減量化方法は、長時間の滞留時間を必要とする
割りには減量化率が劣り、また難脱水性汚泥を生ずる等
の問題があり、最近はほとんど採用されていないのが実
情である。また、活性汚泥を直接オゾン処理して、可溶
化した後、曝気槽に返送する方法(特開平7−1166
85号公報)も提案されているが、オゾン酸化コストが
高額であり、経済的な面などから実用性が乏しいなどの
欠点がある。
One of the means for solving this problem is to reduce the amount of organic sludge, and various means have been proposed for that purpose. As one of means for reducing sludge, there has been a biological biological method for reducing sludge, and an anaerobic digestion method and an aerobic digestion method are known. However, these biological sludge reduction methods have problems that the reduction rate is inferior for a long residence time and that hardly-dewatering sludge is produced. The reality is that there is none. Further, the activated sludge is directly ozone-treated to solubilize it, and then returned to the aeration tank (JP-A-7-1166).
No. 85) is also proposed, but it has drawbacks such as high ozone oxidation cost and poor practicability from the economical aspect.

【0004】[0004]

【解決しようとする課題】有機性廃水の活性汚泥処理法
などが効率的に実施できるようにするためには、そこか
ら生ずる有機性汚泥の減量化も効率的に実施できる、す
なわち減量化が長時間の処理を要せず、また多くの熱エ
ネルギーを要することなく行えるようにする技術の開発
が必要である。本発明は、嫌気性消化法や好気性消化法
のような生物学的な汚泥減量化方法を見直し、生物学的
減量化方法を効果的なものとし、また化学酸化法による
減量化をもっと経済的なものとする新技術を提供するこ
とにある。本発明は、有機性汚泥を効果的かつ経済的に
減量化することによって、汚泥脱水機、焼却炉に持ち込
まれる汚泥量を大きく減少させ汚泥処理工程全体を合理
化することを課題とするものである。
[Problems to be Solved] In order to efficiently carry out the activated sludge treatment method of organic wastewater, the organic sludge produced therefrom can be efficiently reduced, that is, the long-term reduction can be achieved. It is necessary to develop a technology that can be performed without requiring a lot of time and heat energy. The present invention reviews biological sludge reduction methods such as anaerobic digestion method and aerobic digestion method, makes the biological reduction method effective, and makes the reduction by the chemical oxidation method more economical. To provide a new technology that is targeted. An object of the present invention is to reduce the amount of organic sludge effectively and economically, thereby greatly reducing the amount of sludge brought into a sludge dehydrator and an incinerator and rationalizing the entire sludge treatment process. .

【0005】[0005]

【課題を解決するための手段】本発明は、生物学的な嫌
気性消化と化学的酸化による可溶化処理を新規な態様で
結合させ、有機性汚泥の効果的かつ経済的な減量化を実
現したものである。すなわち、本発明は、以下に示す手
段により前記の課題を解決することができた。 (1)有機性汚泥を嫌気性消化工程で嫌気性消化した
後、該消化汚泥にオゾンまたは過酸化水素を添加して可
溶化し、該可溶化汚泥をさらに嫌気性消化することを特
徴とする有機性汚泥の減量化方法であり、(2)有機性
汚泥を嫌気性消化工程で嫌気性消化した後、膜分離手段
により固液分離し、分離された固形消化汚泥にオゾンま
たは過酸化水素を添加して可溶化し、該可溶化汚泥をさ
らに嫌気性消化することを特徴とする有機性汚泥の減量
化方法。
The present invention combines biological anaerobic digestion and solubilization treatment by chemical oxidation in a novel manner to realize an effective and economical reduction of organic sludge. It was done. That is, the present invention was able to solve the above problems by the means shown below. (1) An organic sludge is anaerobically digested in an anaerobic digestion step, and then ozone or hydrogen peroxide is added to the digested sludge to solubilize it, and the solubilized sludge is further anaerobically digested. A method for reducing the amount of organic sludge, which comprises (2) anaerobically digesting organic sludge in an anaerobic digestion step, followed by solid-liquid separation by a membrane separation means, and separating solid digested sludge with ozone or hydrogen peroxide. A method for reducing the amount of organic sludge, which comprises adding and solubilizing the solubilized sludge and further anaerobic digesting the solubilized sludge.

【0006】既に前記したように、原汚泥を直接化学的
に酸化処理して可溶化する場合は、多量のオゾンや過酸
化水素が必要となるが、原汚泥を嫌気性消化した後、そ
の消化汚泥にオゾンまたは過酸化水素を添加して可溶化
する場合には、嫌気性消化によって、原汚泥中の嫌気微
生物に分解され易い部分(通常、汚泥SS重量の60%
程度)が減量化されるので、可溶化に必要なオゾン量は
大幅に少なくてすむ。さらに、嫌気性消化工程は適当な
汚泥濃度に維持することが消化処理を効率的なものにす
るが、この所定の濃度に維持するためには消化汚泥の一
部を嫌気性消化工程から抜き出すことが望ましく、従っ
てこの抜き出した消化汚泥にオゾンまたは過酸化水素を
添加して可溶化することにすれば、さらに可溶化に必要
なオゾン量や過酸化水素量は少なくてすみ、また消化処
理は全体として効果的かつ経済的なものとなる。しかし
て、前記可溶化した消化汚泥をさらに嫌気性消化する工
程に供給し、可溶化汚泥 を微生物により炭酸ガスと水
に分解する。この結果、原汚泥重量の90%以上が減量
化される。
As described above, when the raw sludge is directly chemically oxidized to be solubilized, a large amount of ozone and hydrogen peroxide are required, but after the raw sludge is anaerobically digested, the digestion is performed. When ozone or hydrogen peroxide is added to the sludge to solubilize it, the anaerobic digestion makes it easy to decompose into anaerobic microorganisms in the original sludge (usually 60% of the sludge SS weight).
The amount of ozone required for solubilization can be greatly reduced. Furthermore, maintaining an appropriate sludge concentration in the anaerobic digestion process makes the digestion process efficient, but in order to maintain this predetermined concentration, a part of the digested sludge must be extracted from the anaerobic digestion process. Therefore, if ozone or hydrogen peroxide is added to the extracted digested sludge to solubilize it, the amount of ozone and hydrogen peroxide required for solubilization will be small, and the digestion process will be complete. As effective and economical as. Then, the solubilized digested sludge is supplied to a step for further anaerobic digestion, and the solubilized sludge is decomposed into carbon dioxide gas and water by microorganisms. As a result, 90% or more of the original sludge weight is reduced.

【0007】さらにまた、嫌気性消化工程の中に膜分離
によって消化汚泥を固液分離する手段を設けて、生物学
的に減量化した汚泥を固液分離し、分離液は系外に流出
させ、汚泥の一部を消化工程に移送し、残部を抜き出し
て化学的に酸化して可溶化する方法とすることにより一
層嫌気性消化処理は効果的かつ経済的なものとなる。
Furthermore, a means for solid-liquid separation of digested sludge by membrane separation is provided in the anaerobic digestion process to perform solid-liquid separation of biologically reduced sludge, and the separated liquid is allowed to flow out of the system. The anaerobic digestion process becomes more effective and economical by using a method in which a part of the sludge is transferred to the digestion process and the rest is extracted and chemically oxidized to be solubilized.

【0008】[0008]

【発明の実施の形態】本発明の有機性汚泥の減量化方法
を以下に図により説明する。図1において、有機性汚泥
1をまず第1の嫌気性消化工程2において嫌気性消化
し、生物学的に分解され易い部分を減量化する。嫌気性
消化の処理は、従来知られている嫌気性消化の方法によ
り行うものであって、通常、嫌気性消化によって消化さ
れるのは原汚泥中のSS重量の60%程度である。この
嫌気性消化工程2によって有機性汚泥は低分子の可溶性
の有機化合物となる結果、有機性汚泥はその分減量化さ
れる。第1の嫌気性消化工程2からの嫌気性消化工程2
内の汚泥濃度は汚泥の攪拌が充分に行える6%程度以下
にとどめるのが良い。残部の消化汚泥は系外(化学酸化
工程3)に抜き出しオゾンまたは過酸化水素を添加して
化学酸化工程3により汚泥を可溶化する。可溶化汚泥は
第2の嫌気性消化工程4に移送して嫌気性微生物により
さらに嫌気性消化を行い、炭酸ガスと水に分解する。こ
の結果可溶化処理に回した汚泥については、原汚泥重量
の90%以上が減量化される。第2の嫌気性消化工程4
の消化汚泥は固液分離され、分離液5は系外に排水し、
固形分は残渣汚泥6(減量化汚泥である。)として処理
する。
BEST MODE FOR CARRYING OUT THE INVENTION The method for reducing the amount of organic sludge of the present invention will be described below with reference to the drawings. In FIG. 1, the organic sludge 1 is first anaerobically digested in the first anaerobic digestion step 2 to reduce the amount of the portion that is easily biologically decomposed. The treatment of anaerobic digestion is performed by a conventionally known method of anaerobic digestion, and normally, about 60% of the SS weight in the raw sludge is digested by the anaerobic digestion. By this anaerobic digestion step 2, the organic sludge becomes a low molecular weight soluble organic compound, and as a result, the amount of the organic sludge is reduced accordingly. Anaerobic digestion step 2 from the first anaerobic digestion step 2
The sludge concentration inside should be kept at about 6% or less, where sludge can be sufficiently stirred. The remaining digested sludge is extracted outside the system (chemical oxidation step 3) and ozone or hydrogen peroxide is added to solubilize the sludge in the chemical oxidation step 3. The solubilized sludge is transferred to the second anaerobic digestion step 4 and further anaerobicly digested by anaerobic microorganisms to decompose into carbon dioxide gas and water. As a result, about 90% or more of the weight of the original sludge is reduced in the sludge sent to the solubilization treatment. Second anaerobic digestion step 4
Digested sludge is separated into solid and liquid, and the separated liquid 5 is drained out of the system,
The solid content is treated as residual sludge 6 (reduced sludge).

【0009】本発明の好ましい有機性汚泥の減量化方法
について図2を用いて述べる。前記減量工程において、
第1の嫌気性消化工程2で処理されて出来た消化汚泥を
膜分離や遠心分離などの固液分離工程7により固液分離
し、SSがほとんどゼロの分離液5を得る。膜分離汚泥
8の大部分(還流汚泥9)は第1の嫌気性消化工程2に
還流する。膜分離汚泥の残部(移送汚泥10)は化学酸
化工程3に送り、オゾンまたは過酸化水素を添加して化
学的に可溶化する。可溶化された汚泥は第2の嫌気性消
化工程4に移送して嫌気性微生物により炭酸ガスと水に
分解される。このような操作によって原汚泥重量の95
%以上が減量化される。原汚泥の5重量%程度は分解さ
れない場合が多いので、残渣6(減量化汚泥)として汚
泥脱水機に供給して処分する。また、より好ましい有機
性汚泥の減量化方法についは図3に示した。図3の汚泥
減量化方法の図2の方法との違いは可溶化された汚泥は
第2の嫌気性消化工程4に移送する代わりに第1の嫌気
性消化工程2に戻すもので、第1の嫌気性消化工程2に
より第2の嫌気性消化工程4を兼ねさせる処理法であ
る。
A preferred method for reducing the amount of organic sludge of the present invention will be described with reference to FIG. In the weight reduction step,
The digested sludge produced by the first anaerobic digestion step 2 is subjected to solid-liquid separation in a solid-liquid separation step 7 such as membrane separation or centrifugation to obtain a separation solution 5 having almost zero SS. Most of the membrane separation sludge 8 (reflux sludge 9) is refluxed to the first anaerobic digestion step 2. The remaining portion of the membrane separation sludge (transfer sludge 10) is sent to the chemical oxidation step 3 and chemically solubilized by adding ozone or hydrogen peroxide. The solubilized sludge is transferred to the second anaerobic digestion step 4 and decomposed into carbon dioxide gas and water by anaerobic microorganisms. By such an operation, the weight of the original sludge is 95
% Or more is reduced. Since about 5% by weight of the original sludge is not decomposed in many cases, it is supplied as a residue 6 (reduced sludge) to the sludge dehydrator for disposal. A more preferable method for reducing the amount of organic sludge is shown in FIG. The difference between the sludge reduction method of FIG. 3 and the method of FIG. 2 is that the solubilized sludge is returned to the first anaerobic digestion step 2 instead of being transferred to the second anaerobic digestion step 4. The second anaerobic digestion step 4 is also performed by the anaerobic digestion step 2.

【0010】本発明による有機性汚泥の減量化方法で
は、以下に述べる興味深い効果が認められた。すなわ
ち、図1に示した減量化方法では、最終工程での消化汚
泥の固液分離において、また図2及び図3に示した減量
化方法では、嫌気性消化工程における膜分離おいて、膜
汚染が少なくなることが認められた。その理由はオゾン
または過酸化水素による消化汚泥の化学酸化によって膜
汚染物質が酸化分解されるためと思われる。さらに、図
1や図2における第2の嫌気性消化工程や図3における
可溶化された汚泥を循環させる嫌気性消化工程では、消
化ガス中の硫化水素がやや減少するという効果が認めら
れた。これは、オゾンまたは過酸化水素による化学酸化
により、硫酸還元菌が殺菌されるためと思われる。
In the method for reducing the amount of organic sludge according to the present invention, the following interesting effects were recognized. That is, in the weight reduction method shown in FIG. 1, solid-liquid separation of digested sludge in the final step, and in the weight reduction method shown in FIGS. 2 and 3, membrane separation in the anaerobic digestion step. Was found to be less. The reason seems to be that the membrane pollutants are oxidatively decomposed by the chemical oxidation of digested sludge by ozone or hydrogen peroxide. Further, in the second anaerobic digestion step in FIGS. 1 and 2 and the anaerobic digestion step in which the solubilized sludge is circulated in FIG. 3, the effect that hydrogen sulfide in the digestion gas is slightly reduced was recognized. This is probably because the sulfate-reducing bacteria are killed by chemical oxidation with ozone or hydrogen peroxide.

【0011】[0011]

【実施例】以下に、本発明の有機性汚泥の減量化方法の
実施例を示す。しかし、本発明は以下の実施例によって
制限されるものではない。 図3に基づく実施例:下水の混合生汚泥(固形物濃度2
5.0g/リットル)を前記図3に示した処理フローに
従って処理した。なお、図3では嫌気性消化工程は一つ
であるので単に嫌気性消化工程とした。嫌気性消化工程
で使用する消化槽の容積は150リットル、嫌気性消化
の温度は35℃で、汚泥濃度は4.1〜4.5%、滞留
日数は15日間である。固液分離には膜分離法を適用
し、膜は分画分子量10万のUF膜を用いた。UF膜を
透過するフラックスの線速度は0.1m/日である。な
お、膜汚染が生じた時洗浄する方法は、次亜塩素酸ソー
ダによる化学洗浄による。
EXAMPLES Examples of the method for reducing the amount of organic sludge of the present invention will be shown below. However, the present invention is not limited to the examples below. Example based on FIG. 3: Sewage mixed raw sludge (solids concentration 2
5.0 g / liter) was processed according to the processing flow shown in FIG. In addition, in FIG. 3, since there is only one anaerobic digestion step, only the anaerobic digestion step was used. The volume of the digestion tank used in the anaerobic digestion step is 150 liters, the temperature of the anaerobic digestion is 35 ° C., the sludge concentration is 4.1 to 4.5%, and the retention days are 15 days. A membrane separation method was applied to the solid-liquid separation, and a UF membrane having a cut-off molecular weight of 100,000 was used as the membrane. The linear velocity of the flux passing through the UF membrane is 0.1 m / day. The method of cleaning when the film is contaminated is by chemical cleaning with sodium hypochlorite.

【0012】固液分離された消化汚泥の可溶化はオゾン
酸化法によった。1リットル容積のオゾン酸化槽に固液
分離された消化汚泥の固形物を1.4リットル/日で供
給し、これに消化汚泥の固形物の重量あたり12%のオ
ゾンを供給してオゾン酸化する。この条件で1年間処理
を続けた結果、分解不可能な固形物残渣の発生量は、1
3〜14.6g/日と極めて少なく、可溶化工程への供
給汚泥の約95%が分解された。
Solubilization of the solid-liquid separated digested sludge was carried out by the ozone oxidation method. The digested sludge solid matter that has been solid-liquid separated is supplied at a rate of 1.4 liters / day to an ozone oxidation tank having a volume of 1 liter, and 12% of ozone based on the weight of the digested sludge solid matter is supplied to oxidize it. . As a result of continuing the treatment for 1 year under these conditions, the amount of solid residue that cannot be decomposed is 1
It was extremely low at 3 to 14.6 g / day, and about 95% of the sludge supplied to the solubilization step was decomposed.

【0013】また、消化汚泥を固液分離した際に発生す
る膜分離水はSSゼロの状態であり、極めて清澄であっ
た。固液分離工程における膜透過フラックスの線速度
は、1年間の処理の間、0.1m/日を維持し続けるこ
とができ、洗浄によって回復しないような膜汚染がない
ことが確認された。また、オゾン酸化に変えて過酸化水
素を使用し、過酸化水素添加量を化学酸化槽流入汚泥あ
たり50%添加した場合は、分解不可能な固形物残渣の
発生量は67〜73g/日となりオゾン酸化法よりも劣
るが、実用上の遜色はない。
Further, the membrane-separated water generated when the digested sludge was subjected to solid-liquid separation was in an SS zero state and was extremely clear. It was confirmed that the linear velocity of the membrane-permeating flux in the solid-liquid separation step could be maintained at 0.1 m / day during the treatment for one year, and there was no membrane contamination that would not be recovered by washing. Also, when hydrogen peroxide is used instead of ozone oxidation and the amount of hydrogen peroxide added is 50% per chemical oxidation tank inflow sludge, the amount of solid residue that cannot be decomposed is 67 to 73 g / day. Although it is inferior to the ozone oxidation method, it is not inferior to practical use.

【0014】[0014]

【発明の効果】本発明によれば、有機性汚泥の減量効果
が大きく、生物学的な汚泥減量化の処理時間は短縮さ
れ、また化学的酸化により可溶化におけるオゾンや過酸
化水素の添加費用は、生物学的な汚泥減量化方法を併用
しない場合よりを大幅に削減することができる。また、
膜分離工程における膜汚染をほとんどなくすることがで
きる。
According to the present invention, the effect of reducing the amount of organic sludge is large, the treatment time for biological sludge reduction is shortened, and the addition cost of ozone and hydrogen peroxide in solubilization by chemical oxidation is reduced. Can be significantly reduced compared to the case where the biological sludge reduction method is not used together. Also,
Membrane contamination in the membrane separation step can be almost eliminated.

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

【図1】図1は、本発明において、第1の嫌気性消化工
程、化学酸化工程及び第2の嫌気性消化工程を行う方法
の場合を示す。
FIG. 1 shows a case of a method of carrying out a first anaerobic digestion step, a chemical oxidation step and a second anaerobic digestion step in the present invention.

【図2】図2は、図1に示した本発明において、第1の
嫌気性消化工程の後に膜分離工程を挿入した場合を示
す。
FIG. 2 shows a case where a membrane separation step is inserted after the first anaerobic digestion step in the present invention shown in FIG.

【図3】図3は、図2に示した本発明において、第2の
嫌気性消化工程を第1の嫌気性消化工程により兼用し嫌
気性消化工程とした場合を示す。
FIG. 3 shows a case in which the second anaerobic digestion step is combined with the first anaerobic digestion step in the present invention shown in FIG. 2 to be an anaerobic digestion step.

【符号の説明】[Explanation of symbols]

1 有機性汚泥 2 第1の嫌気性消化工程 3 化学酸化工程 4 第2の嫌気性消化工程 5 分離液 6 残渣汚泥 7 固液分離工程 8 膜分離汚泥 9 還流汚泥 10 移送汚泥 11 嫌気性消化工程 1 Organic Sludge 2 First Anaerobic Digestion Process 3 Chemical Oxidation Process 4 Second Anaerobic Digestion Process 5 Separation Liquid 6 Residual Sludge 7 Solid-Liquid Separation Process 8 Membrane Separation Sludge 9 Reflux Sludge 10 Transfer Sludge 11 Anaerobic Digestion Process

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 有機性汚泥を嫌気性消化工程で嫌気性消
化した後、該消化汚泥にオゾンまたは過酸化水素を添加
して可溶化し、該可溶化汚泥をさらに嫌気性消化するこ
とを特徴とする有機性汚泥の減量化方法。
1. An organic sludge is anaerobically digested in an anaerobic digestion step, and then ozone or hydrogen peroxide is added to the digested sludge to solubilize it, and the solubilized sludge is further anaerobically digested. Method for reducing organic sludge.
【請求項2】 有機性汚泥を嫌気性消化工程で嫌気性消
化した後、膜分離手段により固液分離し、分離された消
化汚泥にオゾンまたは過酸化水素を添加して可溶化し、
該可溶化汚泥をさらに嫌気性消化することを特徴とする
有機性汚泥の減量化方法。
2. The organic sludge is anaerobically digested in an anaerobic digestion step, and then solid-liquid separated by a membrane separation means, and ozone or hydrogen peroxide is added to the separated digested sludge to solubilize it.
A method for reducing the amount of organic sludge, characterized by further anaerobically digesting the solubilized sludge.
JP24470095A 1995-09-22 1995-09-22 How to reduce organic sludge Expired - Fee Related JP3447027B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP24470095A JP3447027B2 (en) 1995-09-22 1995-09-22 How to reduce organic sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP24470095A JP3447027B2 (en) 1995-09-22 1995-09-22 How to reduce organic sludge

Publications (2)

Publication Number Publication Date
JPH0985299A true JPH0985299A (en) 1997-03-31
JP3447027B2 JP3447027B2 (en) 2003-09-16

Family

ID=17122636

Family Applications (1)

Application Number Title Priority Date Filing Date
JP24470095A Expired - Fee Related JP3447027B2 (en) 1995-09-22 1995-09-22 How to reduce organic sludge

Country Status (1)

Country Link
JP (1) JP3447027B2 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000167597A (en) * 1998-12-10 2000-06-20 Japan Sewage Works Agency Anaerobic digestion of organic sludge
JP2002186996A (en) * 2000-12-19 2002-07-02 Kurita Water Ind Ltd Treatment method of organic waste
EP1522528A1 (en) * 2003-10-07 2005-04-13 VA TECH WABAG GmbH Disintegration of anaerobically digested sewage sludge

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000167597A (en) * 1998-12-10 2000-06-20 Japan Sewage Works Agency Anaerobic digestion of organic sludge
JP2002186996A (en) * 2000-12-19 2002-07-02 Kurita Water Ind Ltd Treatment method of organic waste
JP4631162B2 (en) * 2000-12-19 2011-02-16 栗田工業株式会社 Organic waste treatment methods
EP1522528A1 (en) * 2003-10-07 2005-04-13 VA TECH WABAG GmbH Disintegration of anaerobically digested sewage sludge

Also Published As

Publication number Publication date
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