JPH0810778A - Method for deodorizing and purifying sewage and sludge by humic iron-oxygen composite - Google Patents

Method for deodorizing and purifying sewage and sludge by humic iron-oxygen composite

Info

Publication number
JPH0810778A
JPH0810778A JP16578494A JP16578494A JPH0810778A JP H0810778 A JPH0810778 A JP H0810778A JP 16578494 A JP16578494 A JP 16578494A JP 16578494 A JP16578494 A JP 16578494A JP H0810778 A JPH0810778 A JP H0810778A
Authority
JP
Japan
Prior art keywords
sewage
sludge
iron
enzyme
humus
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
JP16578494A
Other languages
Japanese (ja)
Other versions
JP3127281B2 (en
Inventor
Yusuke Ishida
有甫 石田
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.)
ENZAIMU KK
ENZYME KK
Original Assignee
ENZAIMU KK
ENZYME 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 ENZAIMU KK, ENZYME KK filed Critical ENZAIMU KK
Priority to JP06165784A priority Critical patent/JP3127281B2/en
Publication of JPH0810778A publication Critical patent/JPH0810778A/en
Application granted granted Critical
Publication of JP3127281B2 publication Critical patent/JP3127281B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Treatment Of Sludge (AREA)

Abstract

PURPOSE:To inexpensively solve odor removal and to reduce treated sludge to soil by adding an enzyme humic iron-oxygen composite to the sewage derived from living things or excrement, such as sewer water and night soil, and the sludge formed by a biological treatment of the sewage and subjecting the sewage or the sludge to an oxidation treatment by ventilation. CONSTITUTION:The enzyme humic iron-oxygen composite is added to the sewage or the sludge and is subjected to ventilated stirring at about 3m<3> per minute in the case of treatment of the sewage or the sludge formed by the biological treatment of the sewage. The sewage or the sludge is subjected to the oxidation treatment by using >=20% freshly formed sludge at need. The enzyme humic iron-oxygen composite is formed by kneading enzyme humic powder, bivalent iron salts powder and iron-component respectively at <=80%, >=20% and >=2% or are dried within 25% moisture at <=180 deg.C after kneading. The content of the enzyme humic iron-oxygen composite is increased and the amt. thereof to be used is specified to >=1/10000 of the sewage and >=1/1000 of the sludge.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、エンザイム腐植鉄酸素
複合体を、生物または当該排泄物を由来とする汚水の活
性汚泥処理における汚水濃度調整、又は汚泥調質時に使
用して、脱臭および浄化する方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention uses an enzyme humus iron-oxygen complex for deodorization and purification by adjusting the concentration of sewage in activated sludge treatment of sewage derived from living things or the excrement, or during sludge conditioning. It is about how to do it.

【0002】[0002]

【従来の技術】従来から継続してきた活性汚泥法の欠陥
の1つでもある臭気対策の不備は、現状においても未解
決のままである。多量の汚泥が脱水機に移送される間の
変敗、腐敗臭気対策はどうにもならない状態にある。脂
肪酸と2価の鉄と過酸化水素で生成する脂肪酸アルコキ
シラジカルによる脱臭が行われているが、脂肪酸の過酸
化物の臭気が残り、ラジカル連鎖反応におけるラジカル
同士の反応で連鎖反応の終結も早い。また、腐植粉体、
腐植抽出液を汚水または汚泥中で2価の鉄塩類と反応さ
せる例では、腐植鉄錯体の生成量も少なく、腐植酸素複
合体の生成量が少ないために、脱臭、浄化効果が劣って
いた。
2. Description of the Related Art The deficiency of odor control, which is one of the deficiencies of the activated sludge method which has been continued, remains unsolved at present. Countermeasures against spoilage and rotten odors while a large amount of sludge is being transferred to the dehydrator are in control. Deodorization is carried out with fatty acid alkoxy radicals generated from fatty acids, divalent iron and hydrogen peroxide, but the odor of peroxides of fatty acids remains, and the chain reaction also terminates quickly due to the reaction between radicals in the radical chain reaction. . Also humus powder,
In the example of reacting the humus extract with divalent iron salts in sewage or sludge, the amount of humus iron complex produced was small and the amount of humus oxygen complex produced was small, resulting in poor deodorization and purification effects.

【0003】[0003]

【発明が解決しようとする課題】本発明は、臭気を発生
しないように処理された水および生成汚泥が、自然環境
に有用なものとして受け入れられ、還元されるので産業
廃棄物にはならないということを第1の目的とする。ま
た、使用量が少なく、多量の汚水や汚泥の脱臭、浄化処
理ができ、より低コストであることを第2の目的とす
る。
SUMMARY OF THE INVENTION According to the present invention, water and produced sludge treated so as not to generate an odor are accepted as useful for the natural environment and are reduced, so that they do not become industrial waste. Is the first purpose. A second object is to use a small amount, to deodorize and purify a large amount of sewage and sludge, and to lower the cost.

【0004】[0004]

【課題を解決するための手段】本発明の腐植鉄酸素複合
体による汚水、汚泥の脱臭および浄化法は、エンザイム
腐植中に10%以上含有する有機物複合体(分析上の分
類ではフルボ酸に該当する)のすべてを2価の鉄錯体と
し、これに還元型の酸素を付加させた腐植鉄(2価)酸
素複合体とし、これが持つ特性を汚水や汚泥に対して発
揮させるものである。
The method of deodorizing and purifying sewage and sludge using the humus iron oxygen complex of the present invention is an organic substance complex containing 10% or more in enzyme humus (corresponding to fulvic acid in the analytical classification). All of the above) is a divalent iron complex, and a humus iron (divalent) oxygen complex is prepared by adding reduced oxygen to the complex, and the characteristics possessed by the complex are exhibited in sewage and sludge.

【0005】エンザイム腐植と2価鉄塩類との錯体は単
なる2価の鉄とは違い、自己結合や他の有機物との異種
間結合によって発生する過酸化水素で自己酸化を受け、
ヒドロキシラジカルのような活性酸素を発生する。しか
しながら、酸化されて還元型の鉄でなくなれば、結合も
酸化反応もすべて停止してしまう。
Unlike simple divalent iron, the complex of enzyme humus and divalent iron salts undergoes autooxidation with hydrogen peroxide generated by self-bonding or cross-linking with other organic substances,
Generates active oxygen such as hydroxy radicals. However, if it is oxidized to be no reduced iron, all binding and oxidation reactions will be stopped.

【0006】本発明では、エンザイム腐植鉄(2価)錯
体に予め還元型の酸素(一重項酸素)を付加させ、エン
ザイム腐植鉄(2価)酸素複合体を生成させるので、酸
化を受ければヒドロキシラジカルは連鎖反応で自動的に
生成される。従って、酸化脱臭力や浄化能力も持続す
る。
In the present invention, reduced oxygen (singlet oxygen) is added to the enzyme humic iron (divalent) complex in advance to form an enzyme humic iron (divalent) oxygen complex. Radicals are automatically generated by chain reaction. Therefore, the oxidative deodorizing ability and the purifying ability are also maintained.

【0007】エンザイム腐植鉄(2価)酸素複合体を含
む粉体又はペレットを添加した汚水、汚泥中のヒドロキ
シラジカルの発生は、持続性はあるもののその発生率が
穏やかであるので過酸化物の生成は少なく、過酸化物臭
気もない。汚水、汚泥の酸化電位を−100〜+200
mvに長期間維持することができるので、変敗、腐敗に
関与する微生物群の生育を抑制し、良質の微生物群の増
殖を促すことになる。自然環境に喜んで受け入れられる
処理水やコンポストを造ることが容易になり、産業廃棄
物になるものは1つも出ない。
Generation of hydroxy radicals in sewage and sludge containing powder or pellets containing enzyme humic iron (divalent) oxygen complex is persistent but its generation rate is moderate, so that the generation of hydroxyl radicals is low. There is little production and no peroxide odor. Oxidation potential of sewage and sludge is -100 to +200
Since it can be maintained at mv for a long period of time, it suppresses the growth of microbial groups involved in spoilage and decay and promotes the growth of good quality microbial groups. It makes it easier to produce treated water and compost that is willing to be accepted by the natural environment, and none of it becomes industrial waste.

【0008】本発明におけるエンザイム腐植鉄酸素複合
体はエンザイム腐植鉄錯体を作成する際に鉄粉を共存さ
せて混練りを行う。腐植中の分子状酸素および混練り中
に巻き込まれる酸素は還元されて一重項酸素となり、エ
ンザイム腐植鉄錯体に付加させて、エンザイム腐植鉄酸
素複合体になるので、製造コストにも大きな影響を与え
ず、産業廃棄物になるような素材を加えないでもよい。
The enzyme humus iron oxygen complex in the present invention is kneaded by coexisting iron powder when the enzyme humus iron complex is prepared. The molecular oxygen in the humus and the oxygen entrained in the kneading are reduced to singlet oxygen, which is added to the enzyme humus iron complex to form the enzyme humus iron oxygen complex, which also has a large impact on the manufacturing cost. First, it is not necessary to add a material that becomes industrial waste.

【0009】エンザイム腐植鉄酸素複合体の使用量は、
混練り乾燥物で10万分の2以上、汚泥では1万分の2
以上で、混練りのままのものでは上記の2倍以上を使
う。ヒドロキシラジカルの生成が連鎖的に進行している
汚泥をエンザイム腐植鉄錯体の代りに使用する場合で
は、原水や汚泥の20%を加えて攪拌する。再び生成し
た汚泥を新規汚水や汚泥に同じ率で加える繰返しでは5
回以上可能である。従って、その使用量はエンザイム腐
植鉄錯体に比べて1/5以下である。
The amount of enzyme humus iron oxygen complex used is
More than two-thousandth of 100,000 for kneaded and dried material, two-thousandth for sludge
With the above, if the kneaded mixture is used as it is, the above-mentioned amount is used twice or more. When using sludge in which generation of hydroxy radicals proceeds in a chain instead of the enzyme humus iron complex, 20% of raw water or sludge is added and stirred. Repeated addition of regenerated sludge to new wastewater and sludge at the same rate gives 5
It can be done more than once. Therefore, the amount used is 1/5 or less as compared with the enzyme humus iron complex.

【0010】本発明で使用されるエンザム腐植は、落葉
樹の落ち葉と動物由来の分解物が温暖な気候の下で縮合
し、地中に埋蔵されてきた中性腐植を原料とし、バイオ
テクノロジーによって低分子化し、再結合させ、安定化
させた後、粉体としたものである。pHは2.6以下、
酸化電位は+500mV以上で、10%以上の有機物複
合体(分析上の分類におけるフルボ酸に該当)が遊離お
よび鉄錯体として安定な状態で含有されている。有機物
複合体では分子量が2000以上、1000〜2000
および1000以下の含有率は6:3:1である。
The enzam humus used in the present invention is derived from the neutral humus that has been buried in the ground by condensing the leaves of deciduous trees and decomposed products of animal origin under a warm climate. It is made into powder after being molecularized, recombined and stabilized. pH is less than 2.6,
The oxidation potential is +500 mV or more, and 10% or more of an organic compound complex (corresponding to fulvic acid in the analytical classification) is contained in a stable state as a free and iron complex. The organic compound has a molecular weight of 2000 or more, 1000 to 2000
And the content of 1000 or less is 6: 3: 1.

【0011】[0011]

【実施例】以下本発明の実施例について説明する。表1
は、屎尿処理工程での稀釈工程と生物処理後の水質例を
挙げる。沈砂池を出た屎尿を水道水で10倍稀釈を行う
従来法に対して、本発明では10万分の2のエンザイム
腐植鉄酸素複合体を添加した後、0.3m3/日で15分
間曝気した後、一時間放置後、上澄液を曝気槽に移す。
濃縮槽では、汚泥量に対して1万分の2のエンザイム腐
植鉄酸素複合体を加え、1夜毎分0.3m3内外の通気攪
拌を行った後、曝気槽に20%返送し、8時間、毎分
0.3m3で曝気した結果の水質である。
EXAMPLES Examples of the present invention will be described below. Table 1
Examples of water quality after dilution process in biological waste treatment process and biological treatment. In contrast to the conventional method of diluting human waste discharged from a sand basin 10 times with tap water, in the present invention, 2 / 100,000 enzyme humus iron oxygen complex is added and then aerated at 0.3 m 3 / day for 15 minutes. Then, after standing for 1 hour, the supernatant is transferred to an aeration tank.
In the concentration tank, 2 / 10,000 of the enzyme humus iron oxygen complex was added to the amount of sludge, and the mixture was aerated and agitated at a rate of 0.3 m 3 per minute per night, and then returned to the aeration tank at 20% for 8 hours. The water quality is the result of aeration at 0.3 m 3 / min.

【0012】[0012]

【表1】 [Table 1]

【0013】稀釈しないで行った酸化処理の除去率は9
5%以下で、その後の生物処理でも同様の除去率であ
り、エンザイム腐植の添加量が5分の1でも違いが見ら
れなかった。処理場の臭気については、酸化処理後は殆
ど感じられないほど低下し、生物処理の前後および走行
ろ布による脱水中も同様であり、また、エンザイム腐植
の添加量が5分の1でも差が認められなかった。
The removal rate of the oxidation treatment performed without dilution was 9
The removal rate was 5% or less, the removal rate was the same in the subsequent biological treatment, and no difference was observed even when the amount of enzyme humus added was 1/5. The odor of the sewage treatment plant decreased so much that it was hardly felt after the oxidization treatment, and it was the same before and after the biological treatment and during the dehydration with the running filter cloth. Moreover, even if the amount of enzyme humus added was 1/5, there was a difference. I was not able to admit.

【0014】表2は、下水を処理した事例である。本処
理では濃縮槽に添加した結果である。2日間、毎分0.
3m3の曝気を行い、汚泥を活性化した後、20%の汚
泥返送により従来通りの曝気処理を行った後の水質であ
る。BODの除去率は97%で、従来法の82%に比べ
良い結果となった。エンザイム腐植鉄錯体では5分の1
の使用量で大きな違いはなかった。濃縮槽の臭気はエン
ザイム腐植鉄酸素複合体を加えた後、曝気経過時間とと
もに減少し、曝気槽においても従来法より大きく減少し
た。
Table 2 is an example of treating sewage. This is the result of addition to the concentration tank in this treatment. 0 minutes per minute for 2 days.
It is the water quality after aeration of 3 m 3 and activation of sludge, followed by aeration treatment as usual by returning 20% of sludge. The BOD removal rate was 97%, which was a good result as compared with the conventional method of 82%. 1/5 for Enzyme Humic Iron Complex
There was no big difference in the amount used. The odor of the enrichment tank decreased with the passage of aeration after the addition of the enzyme humic iron-oxygen complex.

【0015】[0015]

【表2】 [Table 2]

【0016】[0016]

【発明の効果】本発明は、屎尿や下水汚泥の移送中の臭
気対策を簡単、確実かつ安価な処理方法で解決するばか
りでなく、処理汚泥を価値ある形で土壌に還元できる手
段を提供する点で、その効果は大きい。
INDUSTRIAL APPLICABILITY The present invention not only solves the odor countermeasure during the transfer of human waste and sewage sludge by a simple, reliable and inexpensive treatment method, but also provides a means for returning the treated sludge to the soil in a valuable form. In that respect, the effect is great.

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 下水、屎尿等の生物又は当該排泄物に由
来する汚水、汚水の生物学的処理により生成された汚泥
に、エンザイム腐植鉄酸素複合体を加え、毎分3m3
外の通気により酸化処理を行うことを特徴とする腐植鉄
酸素複合体による汚水、汚泥の脱臭および浄化法。
1. Enzyme humus iron-oxygen complex is added to sewage, wastewater derived from living things such as human waste or the excrement, and sludge produced by biological treatment of sewage, and aeration of 3 m 3 per minute is provided. A method for deodorizing and purifying sewage and sludge using a humic iron-oxygen complex, which is characterized by performing an oxidation treatment.
【請求項2】 下水、屎尿等の生物又は当該排泄物に由
来する汚水、汚水の生物学的処理により生成された汚泥
に、エンザイム腐植鉄酸素複合体を加えて通気攪拌を行
い、新たに生成させた汚泥を20%以上使用して酸化処
理を行うことを特徴とする腐植鉄酸素複合体による汚
水、汚泥の脱臭および浄化法。
2. A sewage derived from organisms such as sewage and human waste, or sewage derived from the excrement concerned, and sludge produced by biological treatment of sewage, an enzyme humus iron-oxygen complex is added and aeration-stirred to newly generate A method of deodorizing and purifying sewage, sludge using a humus iron-oxygen complex, characterized in that an oxidation treatment is performed using 20% or more of the sludge thus made.
【請求項3】 下水、屎尿等の生物又は当該排泄物に由
来する汚水、汚水の生物学的処理により生成された汚泥
に加えるエンザイム腐植鉄酸素複合体は、エンザイム腐
植粉体と2価の鉄塩類粉体と鉄粉とを各々80%以下:
20%以上:2%以上で泥練りするか、又は混練り後、
80℃以下の温度で水分25%内外に乾燥させたもの
で、エンザイム腐植鉄酸素複合体(エンザイム腐植+2
価の鉄+還元型酸素)の含有量を予め増やしたものであ
り、汚水の1万分の1以上、汚泥の千分の1以上を使用
量とすることを特徴とする腐植鉄酸素複合体による汚
水、汚泥の脱臭および浄化法。
3. An enzyme humus iron oxygen complex to be added to sludge produced by biological treatment of organisms such as sewage, human waste, or such excrement, and sludge produced by biological treatment of sewage is an enzyme humus powder and divalent iron. 80% or less of each of salt powder and iron powder:
20% or more: Muddy at 2% or more, or after kneading,
Enzyme humus iron-oxygen complex (Enzyme humus +2
Content of (valent iron + reduced oxygen) has been increased in advance, and the humus iron-oxygen complex is characterized by using more than 1/10000 of sewage and more than one-thousandth of sludge. Deodorization and purification method for sewage and sludge.
JP06165784A 1994-06-27 1994-06-27 Deodorization and purification method of sewage and sludge by humic iron oxygen complex Expired - Fee Related JP3127281B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP06165784A JP3127281B2 (en) 1994-06-27 1994-06-27 Deodorization and purification method of sewage and sludge by humic iron oxygen complex

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP06165784A JP3127281B2 (en) 1994-06-27 1994-06-27 Deodorization and purification method of sewage and sludge by humic iron oxygen complex

Publications (2)

Publication Number Publication Date
JPH0810778A true JPH0810778A (en) 1996-01-16
JP3127281B2 JP3127281B2 (en) 2001-01-22

Family

ID=15818950

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP3127281B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106423720A (en) * 2016-10-12 2017-02-22 珠海凯浩电子有限公司 Capacitive automatic paint immersing machine
CN112156645A (en) * 2020-09-23 2021-01-01 柳州市宝净科技有限公司 Composite biological enzyme deodorant and preparation method thereof

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106423720A (en) * 2016-10-12 2017-02-22 珠海凯浩电子有限公司 Capacitive automatic paint immersing machine
CN112156645A (en) * 2020-09-23 2021-01-01 柳州市宝净科技有限公司 Composite biological enzyme deodorant and preparation method thereof
CN112156645B (en) * 2020-09-23 2021-04-27 柳州市宝净科技有限公司 Composite biological enzyme deodorant and preparation method thereof

Also Published As

Publication number Publication date
JP3127281B2 (en) 2001-01-22

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