JPS604759B2 - Deodorization method - Google Patents
Deodorization methodInfo
- Publication number
- JPS604759B2 JPS604759B2 JP51112877A JP11287776A JPS604759B2 JP S604759 B2 JPS604759 B2 JP S604759B2 JP 51112877 A JP51112877 A JP 51112877A JP 11287776 A JP11287776 A JP 11287776A JP S604759 B2 JPS604759 B2 JP S604759B2
- Authority
- JP
- Japan
- Prior art keywords
- hearth
- wastewater
- slurry
- treated
- present
- 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.)
- Expired
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Treatment Of Biological Wastes In General (AREA)
- Biological Treatment Of Waste Water (AREA)
Description
【発明の詳細な説明】
本発明は排水処理工程中に発生する悪臭の除去方法に係
り、更に詳細には、排水を散布炉床法で処理するに際し
、被処理水を過酸化水素と過酸化カルシウムとのスラリ
ーに接触させることにより処理工程中に発生する悪臭を
除去する方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for removing bad odors generated during a wastewater treatment process. The present invention relates to a method for removing malodors generated during the treatment process by contacting with a slurry with calcium.
現在、一般的に実施されている工場排水および生活排水
等の有機性排水の生物処理方法は、活性汚泥法と散布炉
床法に代表されるが、活性汚泥法は複雑微妙な維持管理
および生成汚泥の処理等で不都合な点が多い。Currently, the biological treatment methods for organic wastewater such as industrial wastewater and domestic wastewater are represented by the activated sludge method and the spray hearth method, but the activated sludge method requires complicated maintenance and production. There are many inconveniences such as sludge treatment.
散布炉床法は運転操作が楽でしかも充填材等の開発で処
理効率の向上も期待できるため近年盛んに利用されるに
至った。この散布炉床法は好気性処理であるために、微
生物の生活環境を常に好気性状態に維持することが不可
欠の要素であるが、好気性雰囲気を長期間維持すること
は困難で、好気性雰囲気が崩れると処理効率の低下は当
然ながら、悪臭や炉床バェが発生し、作業の遅滞だけで
なく社会環境へ悪影響をもたらす結果となる。又、有機
性排水は種々の形態の硫黄化合物や窒素化合物を含んで
居り、還元菌の作用で硫化水素やァミン、アルデヒド等
の悪臭を発生し環境破壊の原因となっている。本発明者
は好気性生物処理法の問題点、つまり好気性状態を如何
に長期間維持させるかの点を重視し鋭意研究の結果、散
布炉床法等充填された炉村表面に付着する微生物膜の酸
化作用による排水処理に極めて有効な脱臭方法を見出し
本発明を完成した。The scattering hearth method has become widely used in recent years because it is easy to operate and can be expected to improve processing efficiency through the development of fillers. Since this spray hearth method is an aerobic process, it is essential to maintain the living environment of microorganisms in an aerobic state at all times, but it is difficult to maintain an aerobic atmosphere for a long period of time, and aerobic If the atmosphere is disrupted, not only will processing efficiency drop, but bad odors and hearth dust will occur, which will not only delay work but also have a negative impact on the social environment. In addition, organic wastewater contains various forms of sulfur compounds and nitrogen compounds, and due to the action of reducing bacteria, hydrogen sulfide, amines, aldehydes, etc. generate bad odors, causing environmental destruction. The present inventor has focused on the problems of aerobic biological treatment, that is, how to maintain an aerobic state for a long period of time, and as a result of intensive research, we have found that microorganisms that adhere to the surface of a filled hearth using the spray hearth method etc. The present invention was completed by discovering an extremely effective deodorizing method for wastewater treatment using the oxidation effect of membranes.
本発明は後述する方法で調整された薬剤を排水中に添加
するだけで悪臭を除去し、又その発生源を断つことがで
き、尚微生物の生活環境を良化するので処理効率を向上
させ得ることのできるものである。即ち、本発明は有機
性排水を固定された生物膜で好気的処理をするに際し、
被処理水に過酸化水素と過酸化カルシウムとのスラリー
を添加することを特徴とする防臭法である。The present invention can remove bad odors and cut off the source of the bad odor by simply adding a chemical prepared by the method described below to wastewater, and also improves the living environment of microorganisms, thereby improving treatment efficiency. It is something that can be done. That is, in the present invention, when aerobically treating organic wastewater with a fixed biofilm,
This is an odor control method characterized by adding a slurry of hydrogen peroxide and calcium peroxide to the water to be treated.
本発明は機構的には発生した臭気が大気中に放散する前
に液中で酸化分解させるものであるが、散布炉床法にお
いて被処理水が炉床に散布される前段階でポンプにより
配管輸送される排水中に添加されたスラリーは均一に混
合し炉床に散布され、炉床通過中にその一部(特に過酸
化カルシウム)が炉材表面の生物膜に付着し微生物の生
活環境を長期間にわたって好気性雰囲気に維持すること
ができる。Mechanistically, the present invention oxidizes and decomposes the generated odor in the liquid before dissipating it into the atmosphere, but in the spray hearth method, the water to be treated is installed in the pipes by a pump before being sprayed on the hearth. The slurry added to the transported wastewater is mixed uniformly and sprinkled on the hearth, and while passing through the hearth, some of it (especially calcium peroxide) adheres to the biofilm on the surface of the furnace material and creates a living environment for microorganisms. Can be maintained in an aerobic atmosphere for long periods of time.
またその付着した過酸化カルシウムの分解により、炉床
が酸性側に低下するのを防ぐため真菌類の過剰増殖もな
く炉床が閉塞して臭気を発生することはない。また炉床
内の遊休部分の嫌気性菌の異常増殖および散水停止時の
炉床内生物膜の腐敗等を防ぐことができ、これらに伴う
臭気発生の恐れもない。炉床内を通過した未反応、未吸
着の該スラリーは、処理水と共に処理水受槽に流下し、
剥離汚泥を多量に含む嫌気性のつよい受槽の環境を改善
する。Furthermore, the decomposition of the adhering calcium peroxide prevents the hearth from becoming acidic, so there is no overgrowth of fungi, and the hearth is not clogged and no odor is generated. In addition, it is possible to prevent the abnormal growth of anaerobic bacteria in the idle portion of the hearth and the decay of the biofilm in the hearth when watering is stopped, and there is no fear of the occurrence of odors associated with these. The unreacted and unadsorbed slurry that has passed through the hearth flows down into the treated water receiving tank together with the treated water.
Improve the environment of a strong anaerobic tank containing a large amount of stripped sludge.
しかし、被処理水に添加する該スラリー濃度は、その殺
菌作用を考慮し、炉床内の生物膜を破壊しない程度に制
限しなければならない。また、処理水受槽から発生する
臭気がひどい場合は、該受槽に該スラリーをあらためて
添加することにより、臭気を容易に抑えることが出来る
。However, the concentration of the slurry added to the water to be treated must be limited to an extent that does not destroy the biofilm in the hearth, taking into account its bactericidal effect. Further, if the odor generated from the treated water receiving tank is severe, the odor can be easily suppressed by adding the slurry to the receiving tank again.
本発明に用いる過酸化水素、過酸化カルシウムの濃度お
よび配合比は排水の組成により一概に決定できないが、
炉床内を通過する該ス・ラリー濃度は過酸化水素分とし
て10■剛以下に保つように調整する。処理水受槽に添
加する該スラリーは、濃度による制約は受けない。本発
明は散布炉床法だけでなく回転円板法等の処理方法にも
応用でき、極めて有利に悪臭を除去できるものである。Although the concentration and blending ratio of hydrogen peroxide and calcium peroxide used in the present invention cannot be determined unconditionally depending on the composition of the wastewater,
The concentration of the slurry passing through the hearth is adjusted to keep the hydrogen peroxide content below 10 μg. The slurry added to the treated water receiving tank is not restricted by concentration. The present invention can be applied not only to the scattering hearth method but also to treatment methods such as the rotating disk method, and can remove bad odors extremely advantageously.
以下本発明を実施例を示し具体的に説明する。The present invention will be specifically explained below with reference to Examples.
実施例 1食品加工業の廃水を、プラスチック製炉村(
客鏡約2血が)を用いた高速散布炉床法により処理し、
従来はほぼ順調に処理が行われて来たが、廃水のCOD
が上昇し、更にこれに気温の上昇が重なって炉床近辺で
かなりの悪臭を発生するようになつていた。Example 1 Wastewater from the food processing industry is recycled into a plastic furnace village (
Treated by high-speed scattering hearth method using a mirror (approximately 2 blood),
Until now, treatment had been carried out almost smoothly, but the COD of wastewater
This, combined with the rise in temperature, caused a considerable odor to be emitted near the hearth.
そこで、散布炉床の前の貯溜槽(容積1■M3)中に、
50%過酸化カルシウムlk9、35%過酸化水素lk
9を水100〆に加え混合した液を加えた。Therefore, in the storage tank (volume 1 M3) in front of the spray hearth,
50% calcium peroxide lk9, 35% hydrogen peroxide lk
9 was added to 100 ml of water and a mixed solution was added.
Claims (1)
に際し、被処理水に過酸化水素と過酸化カルシウムとの
スラリーを添加することを特徴とする防臭法。1. An odor control method characterized by adding a slurry of hydrogen peroxide and calcium peroxide to the water to be treated when organic wastewater is aerobically treated with a fixed biofilm.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP51112877A JPS604759B2 (en) | 1976-09-22 | 1976-09-22 | Deodorization method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP51112877A JPS604759B2 (en) | 1976-09-22 | 1976-09-22 | Deodorization method |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS5339648A JPS5339648A (en) | 1978-04-11 |
JPS604759B2 true JPS604759B2 (en) | 1985-02-06 |
Family
ID=14597757
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP51112877A Expired JPS604759B2 (en) | 1976-09-22 | 1976-09-22 | Deodorization method |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS604759B2 (en) |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5834087A (en) * | 1981-08-21 | 1983-02-28 | Nippon Peroxide Co Ltd | Method of preventing generation of filter bed fly in trickling filter process |
CN104560051A (en) * | 2013-10-12 | 2015-04-29 | 中环循(北京)环境技术中心 | Preparation method of oxygen slow release preparation for repairing of contaminated site |
-
1976
- 1976-09-22 JP JP51112877A patent/JPS604759B2/en not_active Expired
Also Published As
Publication number | Publication date |
---|---|
JPS5339648A (en) | 1978-04-11 |
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