JPS61209093A - Pretreatment of anaerobic treatment - Google Patents

Pretreatment of anaerobic treatment

Info

Publication number
JPS61209093A
JPS61209093A JP60049701A JP4970185A JPS61209093A JP S61209093 A JPS61209093 A JP S61209093A JP 60049701 A JP60049701 A JP 60049701A JP 4970185 A JP4970185 A JP 4970185A JP S61209093 A JPS61209093 A JP S61209093A
Authority
JP
Japan
Prior art keywords
group
anaerobic
treatment
anaerobic treatment
particle size
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
JP60049701A
Other languages
Japanese (ja)
Inventor
Itoku Mori
毛利 威徳
Ryozo Mukai
向 良造
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.)
NIPPON SUIKO KK
Original Assignee
NIPPON SUIKO KK
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 NIPPON SUIKO KK filed Critical NIPPON SUIKO KK
Priority to JP60049701A priority Critical patent/JPS61209093A/en
Publication of JPS61209093A publication Critical patent/JPS61209093A/en
Pending legal-status Critical Current

Links

Classifications

    • Y02W10/12

Abstract

PURPOSE:To advance treatment efficiently, by grinding the solid substance contained in org. sewage so as to obtain an average particle size of 30mum or less. CONSTITUTION:A solid substance is ground so as to obtain an untreated group with a particle size of 500-1,000mum, a group with 50-100mum (ground by a homomixer), a group with 20-30mum, a group with 5-10mum and a group with 1-2mum on the basis of an average particle size. Anaerobic treatment is applied to these groups to enable the enhancement of treatment effect.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、有機性汚水中の固形物を物理的に粉砕するこ
とによって該有機性汚水の嫌気性処理を効率良く進行さ
せることのできる前処理方法に関するものである。
[Detailed Description of the Invention] [Industrial Application Field] The present invention provides a method for efficiently proceeding anaerobic treatment of organic sewage by physically crushing solids in the organic sewage. This relates to a processing method.

〔従来の技術〕[Conventional technology]

嫌気性処理は嫌気性消化法及び嫌気性ラグーン法に分類
されるが、これらのうち嫌気性消化法は有機物濃度の高
い産業廃水例えばアルコール蒸留廃水、洗毛廃水、し尿
等の処理に利用されている。
Anaerobic treatment is classified into anaerobic digestion method and anaerobic lagoon method. Of these, anaerobic digestion method is used to treat industrial wastewater with a high concentration of organic matter, such as alcohol distillation wastewater, hair washing wastewater, human waste, etc. There is.

該嫌気性消化法は、その生成汚泥が有機肥料として利用
できしかも衛生面でも問題がないといった利点を具備し
つつも、残念なことに処理に長時間を要する等の未解決
問題を残している。
Although the anaerobic digestion method has the advantage that the sludge produced can be used as organic fertilizer and there are no hygiene problems, it unfortunately still has unresolved problems such as the long processing time required. .

そこで上述の如き問題点を解決すべく種々の方面から広
範な研究が続けられているが、その成果の1つとして特
公昭57−1319号公報に開示されている様な方法を
挙げることができる。この方法は、嫌気性消化を、(1
)有機性廃棄物にアルカリを加えて加熱処理する分解工
程、(2)分解処理したスラリーを液化菌と接触させる
液化工程、(3)液化スラリーをガス化園と接触させる
ガス化工程に分けて進行させることによって、該嫌気性
消化の効率改善を図り処理に要する時間の短縮化に資す
るものであるが、要は嫌気性消化反応自体を把握しこれ
を調節しようとする立場から検討されたものである。
Therefore, in order to solve the above-mentioned problems, extensive research is being continued from various directions, and one of the results of this research is the method disclosed in Japanese Patent Publication No. 1319/1983. . This method performs anaerobic digestion (1
) The decomposition process involves adding alkali to organic waste and heat-treating it, (2) the liquefaction process involves bringing the decomposed slurry into contact with liquefaction bacteria, and (3) the gasification process involves bringing the liquefied slurry into contact with a gasification garden. By allowing the anaerobic digestion to proceed, it helps to improve the efficiency of the anaerobic digestion and shorten the time required for processing, but the point is that it was studied from the standpoint of understanding the anaerobic digestion reaction itself and trying to adjust it. It is.

ところでこの様な嫌気性処理を行なうに当たっては、該
処理槽内を撹拌しつつ行なわれるのが一般的である。該
撹拌操作は、嫌気性処理効率のより一層の改善を図るべ
く、有機性汚水中の有機物。
By the way, when performing such anaerobic treatment, it is common to carry out the treatment while stirring the inside of the treatment tank. This stirring operation is performed to remove organic matter from organic wastewater in order to further improve the anaerobic treatment efficiency.

固形物、嫌気性消化法等を処理槽中に均一分散させるご
とを主な目的として行なわれる。
The main purpose is to uniformly disperse solids, anaerobic digestion, etc. in the treatment tank.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

しかるに上述の如き一般的撹拌操作にあっては、有機物
や固形物等を粉砕しより微細化するといった効果が発揮
されない為、該有機物や固形物等が単に混合・分散され
るに過ぎず、従って上述の如き撹拌を行なったとしても
、該有機物とこれを消化する嫌気性消化菌との間の接触
関係か必ずしも有効に保障されるとは限らず、上記開示
されている様fl改良方法と組み合わせたとしても期待
される程の処理効率の向上効果を得る迄には至っていな
いのか現状である。この様な状況であるから有機性汚水
中の有機物と、これを消化する嫌気性菌とに確実且つ有
効な接触関係を保障する様な漸新な方法の登場が待たれ
ていた。
However, in the above-mentioned general stirring operation, the effect of pulverizing organic substances and solid substances into finer particles is not achieved, so the organic substances and solid substances are merely mixed and dispersed. Even if the above-mentioned stirring is performed, the contact relationship between the organic matter and the anaerobic digestive bacteria that digest it is not necessarily guaranteed effectively, and it is difficult to combine it with the fl improvement method as disclosed above. Even if it were, the current situation is that it has not yet reached the point where it has achieved the expected effect of improving processing efficiency. Under these circumstances, the emergence of a new method that would ensure reliable and effective contact between the organic matter in organic wastewater and the anaerobic bacteria that digest it has been awaited.

本発明はこうした事情を考慮してなされたものであって
、有機物と嫌気性消化菌の有効な接触を保障すべく有機
性汚水中の固形物を物理的に粉砕することによって、嫌
気性処理効率の向上を図ろうとするものである。
The present invention was made in consideration of these circumstances, and it improves the efficiency of anaerobic treatment by physically crushing solids in organic wastewater to ensure effective contact between organic matter and anaerobic digestive bacteria. The aim is to improve the

〔問題点を解決するための手段〕[Means for solving problems]

しかして本発明に係る嫌気性処理の前処理方法とは、有
機性汚水に含まれる固形物の平均粒度を30μm以下に
粉砕する点にその要旨が存在するものである。
However, the gist of the pretreatment method for anaerobic treatment according to the present invention lies in pulverizing the solids contained in organic wastewater to an average particle size of 30 μm or less.

〔作用〕[Effect]

次に本発明を完成するに至る迄の経緯を辿りつつ本発明
の構成及び作用・効果を明らかにしていく。
Next, we will clarify the structure, operation, and effects of the present invention while tracing the process that led to the completion of the present invention.

本発明者等は、嫌気性消化効率の向上を目的とする研究
はもとより水処理全般に渡って長年研究を続けてきたが
、その過程で有機性汚水中に存在する固形物を物理的手
段によって粉砕すれば該処理効率が大幅に向上すること
を知った。さて次に問題となるのは、上記粉砕の程度言
い換えると上記固形物の好適大きさを奈辺に設定するか
という点である。そこで上記粉砕の程度を規定すべく、
粉砕手段を色々変更することによって粉砕程度を調整し
、固形物の粒子径(平均粒子径として取扱う)の異なる
各種有機性汚水を使った。そして嫌気性消化の処理効率
につき検討し、更に鋭意研究を重ねた結果本発明を完成
するに至った。
The present inventors have been conducting research for many years not only with the aim of improving the efficiency of anaerobic digestion but also with water treatment in general. I learned that pulverization can greatly improve the processing efficiency. Now, the next issue is how to set the degree of pulverization, in other words, the preferred size of the solid material. Therefore, in order to specify the degree of pulverization,
The degree of pulverization was adjusted by changing the pulverization means, and various organic wastewaters with different solid particle sizes (treated as average particle sizes) were used. After studying the treatment efficiency of anaerobic digestion and conducting further intensive research, the present invention was completed.

この間の事情を更に詳細に説明する。The circumstances during this time will be explained in more detail.

本発明者等は、平均粒子径として(1) 500−10
00μm無処理群、 (2350〜100μm群(ホモ
ミキサーにて粉砕二以下同じ)、(3)20〜30μm
群、(4)5〜10μm群、 (5) 1〜2μm群の
ものを作成し、夫々に嫌気性処理を施こしたところ、後
記第1表から明らかな様に平均粒径20〜30μmまで
粉砕したものにあっては、50〜100μmまで粉砕し
たものに比べて嫌気性処理効率が飛躍的に向上している
ことを知った。この知見から推定すると有機性汚水の固
形物を大略30μm以下まで粉砕すると該処理効率の向
上が図れるとの結論を得るに至った。けだし固形物を3
0μm以下とすると、該固形物の表面積が増えることに
なるから、嫌気性消化菌の活動の場も増え、結局のとこ
ろ嫌気性処理効率が全体として向上するものと考えられ
る。
The present inventors have determined that the average particle diameter is (1) 500-10
00 μm untreated group, (2350-100 μm group (same as below 2 crushed with homomixer), (3) 20-30 μm
Group, (4) 5-10 μm group, and (5) 1-2 μm group were prepared and subjected to anaerobic treatment, and as is clear from Table 1 below, the average particle size was 20-30 μm. It was found that the anaerobic treatment efficiency of the pulverized material was dramatically improved compared to that of the pulverized material to a size of 50 to 100 μm. Inferring from this knowledge, we have come to the conclusion that the treatment efficiency can be improved by pulverizing the solids of organic wastewater to approximately 30 μm or less. 3 solid foods
When the diameter is 0 μm or less, the surface area of the solid material increases, which increases the number of active areas for anaerobic digestive bacteria, which is thought to ultimately improve the anaerobic treatment efficiency as a whole.

そしてこの粉砕に当たって固形物や嫌気性消化菌体内に
束縛されているプロテアーゼやセルラーゼ等の酵素が一
部開放され、その為汚水中の炭水化物や蛋白質等の消化
が起こるといったことも該処理効率向上の一因であるも
のと考えられる。
Furthermore, during this pulverization, enzymes such as proteases and cellulases that are bound in the solids and anaerobic digestive bacteria are partially released, and as a result, carbohydrates and proteins in the wastewater are digested, which also improves the treatment efficiency. This is thought to be a contributing factor.

この様な酵素作用に着目すると、嫌気性処理の前後にお
いてプロテアーゼやセルラーゼ等の酵素を積極的に加え
ることによって、処理効率のより一層の向上を図ること
ができる。ここに言う酵素とは、セルラーゼやプロテア
ーゼをはじめとして有機性汚水に含まれる炭水化物、蛋
白質、脂質等を分解する酵素であればどの様なものでも
良い。
Focusing on such enzymatic action, treatment efficiency can be further improved by actively adding enzymes such as protease and cellulase before and after anaerobic treatment. The enzyme referred to herein may be any enzyme, including cellulase and protease, as long as it decomposes carbohydrates, proteins, lipids, etc. contained in organic wastewater.

以下実施例を説明することによって本発明をより鮮明に
していく。
The present invention will be made clearer by describing examples below.

〔実施例〕〔Example〕

焼酎蒸留廃液を用いて、これを(1)対象群(無処理群
)とし、(2)該焼酎蒸留廃液をホモミキサー〔特殊機
化工業(株)社製、タイプ:HV−M型〕により2分間
、aooorpmで撹拌粉砕した群、(3)同じく3分
間、3QQQrpmで撹拌粉砕した群、(4)同6分間
 3000rPmで撹拌粉砕した群、(5)同15分間
、aooorpmで撹拌粉砕した群に分割しく夫々ニツ
イテ大略BOD:297571v//i’、COD:1
2937ダ/l、55二30807ダ/1.全有機物蓋
:56681M1/l  であった)、以下の様に検討
した。
Using shochu distillation waste liquid, this was (1) a target group (untreated group), and (2) the shochu distillation waste liquid was mixed with a homomixer [manufactured by Tokushu Kika Kogyo Co., Ltd., type: HV-M type]. A group that was agitated and pulverized at aooorpm for 2 minutes, (3) a group that was agitated and pulverized at 3QQQrpm for the same 3 minutes, (4) a group that was agitated and pulverized at 3000 rpm for 6 minutes, and (5) a group that was agitated and pulverized at aooorpm for 15 minutes. Roughly divided into two parts: BOD: 297571v//i', COD: 1
2937 da/l, 55230807 da/1. The total organic matter content was 56,681 M1/l), and was investigated as follows.

上記(1)〜(5)の焼酎蒸留廃液51を使用し嫌気性
処理を行なったところ第1表に示す様な結果を得た。但
し全有機物量: 17 g/日添加、BOD:8.94
g/日添加、容積負荷1.44kQ/ゴ・日といった条
理条件とした。また特に処理日数とガス発生量の関係を
VJ1図に示す。
When anaerobic treatment was performed using the shochu distillation waste liquid 51 from (1) to (5) above, the results shown in Table 1 were obtained. However, total organic matter amount: 17 g/day addition, BOD: 8.94
The conditions were as follows: addition: g/day, volumetric load: 1.44 kQ/day. In particular, the relationship between the number of processing days and the amount of gas generated is shown in diagram VJ1.

第1表及び第1図より明らかfl様に、A3〜&5の群
においては&1及び&2群と比較してCODの点でもガ
ス発生量の点でも良好な成績であることが分かった。
As is clear from Table 1 and FIG. 1, the A3 to &5 groups had better results than the &1 and &2 groups in terms of both COD and gas generation.

〔発明の効果〕〔Effect of the invention〕

本発明は、以上の様に構成されているので、有機性汚水
の嫌気性処理効率を向上させることができた。
Since the present invention is configured as described above, it is possible to improve the efficiency of anaerobic treatment of organic wastewater.

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

第1図は処理日数とガス発生量の関係を示したグラフで
ある。
FIG. 1 is a graph showing the relationship between the number of processing days and the amount of gas generated.

Claims (1)

【特許請求の範囲】[Claims] 有機性汚水に含まれる固形物を、その平均粒度が30μ
m以下となる様に粉砕することを特徴とする嫌気性処理
の前処理方法。
The average particle size of solids contained in organic wastewater is 30μ.
A pretreatment method for anaerobic treatment, characterized by pulverizing it to a size of less than m.
JP60049701A 1985-03-12 1985-03-12 Pretreatment of anaerobic treatment Pending JPS61209093A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60049701A JPS61209093A (en) 1985-03-12 1985-03-12 Pretreatment of anaerobic treatment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60049701A JPS61209093A (en) 1985-03-12 1985-03-12 Pretreatment of anaerobic treatment

Publications (1)

Publication Number Publication Date
JPS61209093A true JPS61209093A (en) 1986-09-17

Family

ID=12838486

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60049701A Pending JPS61209093A (en) 1985-03-12 1985-03-12 Pretreatment of anaerobic treatment

Country Status (1)

Country Link
JP (1) JPS61209093A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0987224A3 (en) * 1998-09-03 2000-11-02 Nkk Corporation Method and apparatus for removing phosphorus and nitrogen from wastewater

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0987224A3 (en) * 1998-09-03 2000-11-02 Nkk Corporation Method and apparatus for removing phosphorus and nitrogen from wastewater

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