JPH0611440B2 - Sewage treatment method - Google Patents

Sewage treatment method

Info

Publication number
JPH0611440B2
JPH0611440B2 JP60019139A JP1913985A JPH0611440B2 JP H0611440 B2 JPH0611440 B2 JP H0611440B2 JP 60019139 A JP60019139 A JP 60019139A JP 1913985 A JP1913985 A JP 1913985A JP H0611440 B2 JPH0611440 B2 JP H0611440B2
Authority
JP
Japan
Prior art keywords
filter medium
phosphorus
iron
sewage
contact
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 - Lifetime
Application number
JP60019139A
Other languages
Japanese (ja)
Other versions
JPS61178092A (en
Inventor
猛 西口
展利 前田
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.)
Unitika Ltd
Original Assignee
Unitika 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 Unitika Ltd filed Critical Unitika Ltd
Priority to JP60019139A priority Critical patent/JPH0611440B2/en
Priority to KR1019860000615A priority patent/KR860006403A/en
Publication of JPS61178092A publication Critical patent/JPS61178092A/en
Publication of JPH0611440B2 publication Critical patent/JPH0611440B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds
    • 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

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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は下水,し尿系汚水,産業汚水等の汚水から有機
物と同時にリンを高効率に除去する汚水の処理方法に関
するものである。
TECHNICAL FIELD The present invention relates to a method for treating sewage, night soil-based sewage, industrial sewage, and other sewage, in which phosphorus is removed at the same time as organic substances with high efficiency.

(従来の技術,発明が解決しようとする問題点) 近年,河川,湖沼あるいは海域における富栄養化の問題
が大きく取り上げられている。特に琵琶湖,霞ヶ浦等の
湖沼では富栄養化が著しく進行しており,この富栄養化
の原因の一つとしてリンがあげられ、すでに滋賀県,茨
城県では県条令でリン規制が実施されている。
(Problems to be Solved by Conventional Techniques and Inventions) In recent years, the problem of eutrophication in rivers, lakes and marine areas has been widely taken up. In particular, eutrophication has been remarkably progressing in lakes such as Lake Biwa and Lake Kasumigaura. Phosphorus has been cited as one of the causes of this eutrophication. .

従来,リンの除去方法については,一般的に生物処理を
終えた汚水にCa,Al,Fe塩等の凝集剤を加えて,凝集沈
澱させる方法が採用されている。しかしながら,この方
法は凝集剤の注入により難脱水性汚泥が多量に発生し,
その処分にかなりの経費を要するために,経済的な方法
ではない。そのため,簡易で効率的なリンの処理法の開
発が望まれている。
Conventionally, as a method for removing phosphorus, a method in which a coagulant such as Ca, Al, or Fe salt is added to sewage that has been subjected to biological treatment to coagulate and precipitate is generally adopted. However, this method produces a large amount of non-dehydrating sludge due to the injection of coagulant,
It is not an economical method because its disposal requires considerable expense. Therefore, development of a simple and efficient phosphorus processing method is desired.

最近,嫌気−好気処理の繰り返しによる微生物のリン過
剰摂取作用を利用した生物脱リン法や骨炭,リン鉱石を
用いた晶析脱リン法が研究されている。しかし,これら
の処理法は管理がむつかしいことや,安定した処理効果
を得ることが困難であるなどの欠点がある。また,プラ
スチック,繊維や石塊を接触濾材とした循環式接触曝気
法による汚水処理も有機物の除去処理として広く用いら
れてはいるが,リン除去の効果はなく,リン除去のため
には別途の高次処理が必要であった。
Recently, studies have been conducted on a biological dephosphorization method utilizing the excessive phosphorus uptake effect of microorganisms by repeated anaerobic-aerobic treatment and a crystallization dephosphorization method using bone charcoal and phosphate rock. However, these treatment methods have drawbacks such as difficult management and difficulty in obtaining a stable treatment effect. In addition, although sewage treatment by a circulating contact aeration method using plastic, fiber or lumps as a contact filter medium is also widely used as an organic matter removal treatment, it does not have the effect of removing phosphorus, and a separate phosphorus removal method is used for removing phosphorus. Higher level treatment was required.

(問題点を解決するための手段) 本発明者等は,上記のような実情に鑑み,従来法の欠点
を解消するために鋭意研究した結果,本発明を完成した
のである。すなわち,本発明は接触濾材として鉄濾材の
単独又はこれを主材に充填し,該鉄濾材の表面積に対す
るリンの負荷が1.0g/m2・日以下になるように汚水
を循環曝気処理して汚水中の有機物とリンを除去するこ
とを特徴とする汚水の処理方法を提供するものであり,
これによって汚水からの有機物とリンとの除去を高効率
で安定したものとすることが可能となったのである。
(Means for Solving Problems) The inventors of the present invention have completed the present invention as a result of earnest research in order to solve the drawbacks of the conventional methods in view of the above circumstances. That is, in the present invention, an iron filter medium alone or as a main material is filled as a contact filter medium, and sewage is circulated and aerated so that the phosphorus load on the surface area of the iron filter medium is 1.0 g / m 2 · day or less. The present invention provides a method for treating sewage, which is characterized by removing organic matter and phosphorus in the sewage.
This has made it possible to make the removal of organic matter and phosphorus from wastewater highly efficient and stable.

以下に本発明の方法を図面によって詳細に説明する。Hereinafter, the method of the present invention will be described in detail with reference to the drawings.

第1図は本発明の汚水中のリンの除去方法に用いるとこ
ろの循環式接触曝気法による汚水処理装置の一例の概略
図を示すもので,接触濾材としてのプラスチック濾材や
石塊の濾材を用いて生物膜汚水処理するところの広く知
られた循環曝気式汚水処理装置である。すなわち,汚水
は導入管1より接触濾材槽2の隔壁3で仕切られた曝気
室4に入り,循環する汚水とともに散気管5より吹き出
す空気泡のエアーリフト効果で,接触濾材槽2に入り、
接触濾材6を通過して循環曝気し,接触濾材表面に微生
物を着生させながら汚水中の有機物を処理するものであ
り,循環接触曝気した処理水は処理水排出口7より排出
するか,又は沈澱槽(図指省略)に導入し,その後放水
される。
FIG. 1 is a schematic view of an example of a sewage treatment apparatus by a circulating contact aeration method used in the method for removing phosphorus in wastewater according to the present invention, in which a plastic filter material or a stone block filter material is used as a contact filter material. It is a well-known circulating aeration type sewage treatment device for treating biofilm sewage. That is, the sewage enters the aeration chamber 4 which is partitioned by the partition wall 3 of the contact filter medium tank 2 from the introduction pipe 1, and enters the contact filter medium tank 2 by the air lift effect of the air bubbles blown out from the diffuser pipe 5 together with the circulating sewage.
The organic matter in the wastewater is treated while passing through the contact filter medium 6 to circulate and aerate the surface of the contact filter medium, and the treated water subjected to the circulation contact aeration is discharged from the treated water discharge port 7, or It is introduced into a settling tank (figure omitted) and then discharged.

本発明の特徴は,この接触濾材6に鉄濾材を主材として
使用することと,鉄接触濾材の充填量をリンの処理量か
ら算出することと,鉄接触濾材によるリンの除去は鉄接
触濾材の表面積と汚水の循環曝気が最も関与するもので
あるということである。すなわち,鉄濾材表面積に対す
るリンの負荷が1.0g/m2・日以下になるように鉄接
触濾材を充填し,汚水を循環曝気することにより高効率
のリン除去が安定して得られるのである。かくのごと
く,鉄接触濾材に対するリン負荷は1.0g/m2・日以
下で効果があるが,実用的には0.1〜1.0g/m2
日の範囲であり,0.1g/m2・日より小さいと汚水中
のSSや発生汚泥による濾材の目詰まり現象が早くなり,
ひんぱんに濾材洗滌を行うことが必要になる。他方鉄濾
材表面積に対するリンの負荷が1.0g/m2・日より大
きいと脱リン効果が少なくまた汚水を汚水の循環を減じ
た,すなわち全面曝気の場合は同一の曝気量でも処理効
果が少ない。また,プラスチック接触濾材のみを充填し
た場合もリン除去の効果はほとんど得られない。鉄濾材
によるリンの除去機構については明瞭ではないが,鉄接
触濾材表面からのFeイオンの溶出分の汚水中のリンイオ
ン分とが反応して結晶状あるいは非晶状の不溶性リン酸
鉄が形成され,該リン酸鉄が循環曝気することによって
鉄濾材表面の微生物膜に包含され,混然一体となるよう
であり,このことと沈澱槽に汚泥がほとんど流出しなか
ったことより,この鉄接触濾材表面の微生物膜によりFe
イオンの過度の流出を防ぎ,効率の良いリン除去が行わ
れるものと考えられる。
The features of the present invention are that an iron filter medium is used as the main material in the contact filter medium 6, the filling amount of the iron contact filter medium is calculated from the treated amount of phosphorus, and the removal of phosphorus by the iron contact filter medium is performed by the iron contact filter medium. The surface area of sewage and circulation aeration of sewage are the most important factors. That is, high efficiency phosphorus removal can be stably obtained by filling the iron contact filter medium so that the load of phosphorus on the surface area of the iron filter medium is 1.0 g / m 2 · day or less and circulating and aeration of the sewage. . As described above, the phosphorus load on the iron contact filter medium is effective at 1.0 g / m 2 · day or less, but practically 0.1 to 1.0 g / m 2 ·
If it is less than 0.1 g / m 2 · day, the clogging phenomenon of the filter medium due to SS in the wastewater and the generated sludge will be accelerated,
It is necessary to wash the filter medium frequently. On the other hand, if the phosphorus load on the surface area of the iron filter medium is larger than 1.0 g / m 2 · day, the dephosphorization effect is small and the circulation of sewage is reduced, that is, in the case of full aeration, the treatment effect is small even with the same aeration amount. . In addition, the effect of removing phosphorus is hardly obtained when only the plastic contact filter medium is filled. Although the mechanism of phosphorus removal by iron filter media is not clear, crystalline or amorphous insoluble iron phosphate is formed by reacting Fe ion elution from the iron contact filter media with phosphorus ion components in wastewater. , It seems that the iron phosphate is included in the microbial membrane on the surface of the iron filter medium due to the cyclic aeration and becomes a mixed body. This fact and that sludge hardly flows out to the sedimentation tank, the iron contact filter medium Fe on the surface microbial film
It is considered that the excessive outflow of ions is prevented and phosphorus is efficiently removed.

汚水の有機物濃度等に関係があるが,汚水処理実施中に
接触濾材表面の微生物膜が肥厚化しすぎると,リンの除
去効果が低下する傾向がみられるので,接触濾材表面の
微生物は適宜洗浄することが望まれる。接触濾材表面の
洗浄は,逆洗管8を用い多量の空気を流し洗浄する空気
逆洗方式をとるのが一般的である。この逆洗によって濾
材から剥離した汚泥は一週間以上貯留放置してもリンの
放出はほとんどみられず,活性汚泥法により生物脱リン
した貯留汚泥とは著しく異なるものである。
Although it is related to the concentration of organic matter in the sewage, if the microbial film on the surface of the contact filter medium is excessively thickened during the treatment of sewage, the removal effect of phosphorus tends to decrease. Is desired. For cleaning the surface of the contact filter medium, it is general to use an air backwashing method in which a large amount of air is flowed through the backwashing pipe 8 for washing. The sludge separated from the filter medium by this backwash shows almost no phosphorus release even if it is stored and left for one week or more, which is significantly different from the stored sludge biologically dephosphorized by the activated sludge method.

接触濾材として用いる鉄濾材の具体例は,鉄板やパンチ
ングメタル,エキスパンドメタルなどの網目状鉄材ある
いは網目状空隙を有する球形充填物,円筒状充填物など
表面積の多い形態のものが望ましい。また,これらの鉄
濾材は単独で使用するのが好ましいが,プラスチック濾
材と併用することも可能である。この時も鉄濾材の表面
積に対するリンの負荷を前記したごとく1.0g/m2
日以下にすることが必要である。
Specific examples of the iron filter medium used as the contact filter medium are those having a large surface area such as a reticulated iron material such as an iron plate, punching metal or expanded metal, or a spherical filler having a reticulated void or a cylindrical filler. Further, these iron filter media are preferably used alone, but they can be used in combination with a plastic filter media. At this time as well, the load of phosphorus on the surface area of the iron filter medium was 1.0 g / m 2 ·
It should be less than a day.

第2図は汚水処理量を変えることによって鉄濾材表面積
に対するリン負荷(g/m2・日)を変えた場合の汚水中
のリンの除去率の実験値(比較のためのプラスチック濾
材のみのものも記載)で,鉄接触濾材表面積に対するリ
ン負荷は0.1〜1.0g/m2・日の範囲では90%のリ
ン除去率が得られ,実用上は1.0g/m2・日以下で好
ましいことが明瞭である。
Fig. 2 shows experimental values of phosphorus removal rate in sewage when the phosphorus load (g / m 2 · day) to the iron filter medium surface area was changed by changing the amount of treated wastewater (only for plastic filter medium for comparison). in also described), phosphorus load on iron contact filter media surface area is in the range of 0.1 to 1.0 g / m 2 · day were obtained 90% of the phosphorous removal rate, practically the following 2-days 1.0 g / m It is clear that this is preferable.

(実施例) 以下に実施例をあげる。(Example) An example is given below.

実施例1〜2,比較例1〜3 第1図に示す循環式接触曝気槽(容積67)に接触濾材
としてエキスパンドメタルXS-42(鉄材)とプラスチッ
ク濾材(網目状空隙を有する小型円筒物)とを用い,エ
キスパンドメタルとプラスチック濾材との割合を変えて
接触濾材容積を45(充填率67%)となして人工汚水を
用いて循環曝気処理を行った。処理水量は40/日,滞
留時間は40時間とした。その結果を次表に示す。
Examples 1-2 and Comparative Examples 1-3 In the circulating contact aeration tank (volume 67) shown in FIG. 1, expanded metal XS-42 (iron material) as a contact filter medium and plastic filter medium (small cylinder having mesh-like voids) Using and, the ratio of expanded metal and plastic filter media was changed to make the contact filter media volume 45 (filling ratio 67%), and the circulating aeration treatment was performed using artificial sewage. The amount of treated water was 40 / day and the residence time was 40 hours. The results are shown in the table below.

以上の結果,本発明の方法による処理効果は抜群であっ
た。すなわち,実施例1〜2のように鉄濾材表面積に対
するリン負荷が1.0g/m2・日以下にすればリン除去
の効果が大であり,1.5g/m2・日及び1.7g/m2
・日(比較例1,2)ではリン除去率が大きく低下し
た。比較例3として実施したプラスチック濾材のみの充
填ではBOD値は低下したが,リン除去の効果はほとんど
得られなかった。
As a result, the treatment effect of the method of the present invention was outstanding. That is, as in Examples 1 and 2, if the phosphorus load on the surface area of the iron filter medium is 1.0 g / m 2 · day or less, the effect of phosphorus removal is large, and 1.5 g / m 2 · day and 1.7 g are obtained. / M 2
-The phosphorus removal rate significantly decreased on the day (Comparative Examples 1 and 2). The filling of the plastic filter medium alone as Comparative Example 3 lowered the BOD value, but the effect of removing phosphorus was hardly obtained.

実施例3,比較例4〜5 第1図に示すような循環式接触曝気槽(容積5.2)
に接触濾材としてエキスパンドメタルXS-42(鉄材)を
充填濾材容積が約50%(2.6,鉄濾材表面積は約
0.2m2)充填し,汚水は産業排水の活性汚泥処理水
(リン濃度は約3ppm)を用い,循環曝気しながら汚水
処理を行った。処理量は10/日として,鉄濾材表面積
に対するリン負荷は0.15g/m2・日とした。また,この
場合は比較例として全面曝気で,その他は本実施例と同
様ではあるが,鉄接触濾材の下部から曝気して汚水の循
環を減じた場合のもの(比較例4)と,接触濾材として
プラスチック濾材(網目状空隙を有する円筒物)を2.
6充填し、循環曝気した場合のもの(比較例5)も実
施した。その結果を次表に示す。
Example 3, Comparative Examples 4 to 5 Circulating contact aeration tank as shown in FIG. 1 (volume 5.2)
Filled with expanded metal XS-42 (iron material) as a contact filter material, the filter material volume is about 50% (2.6, iron filter material surface area is about 0.2 m 2 ) and the sewage is activated sludge treated water of industrial wastewater (phosphorus concentration). Was used to treat sewage while circulating and aeration. The treatment amount was 10 / day, and the phosphorus load on the surface area of the iron filter medium was 0.15 g / m 2 · day. Further, in this case, the whole surface is aerated as a comparative example, and the other is the same as this example, but the circulation of the waste water is reduced by aeration from the lower part of the iron contact filter medium (Comparative example 4) and the contact filter medium. 1. As a plastic filter material (cylindrical material having mesh-like voids).
6 filling and circulation aeration (Comparative Example 5) were also carried out. The results are shown in the table below.

以上の結果,実施例3のリン除去効果は著しく優れてい
た。また,比較例4のように汚水を循環しない場合に
は,同一の曝気量でも除去効果は低下し,本発明の方法
のように循環曝気すると処理効率が飛躍的に向上し得る
ということが認められ,比較例5のようにプラスチック
濾材のみでは,リンの除去効果は著しく低いものである
ということが認められた。
As a result, the phosphorus removing effect of Example 3 was remarkably excellent. Further, when the wastewater is not circulated as in Comparative Example 4, the removal effect is reduced even with the same aeration amount, and it is recognized that the circulation aeration as in the method of the present invention can dramatically improve the treatment efficiency. It was confirmed that the effect of removing phosphorus was remarkably low only with the plastic filter medium as in Comparative Example 5.

(発明の効果) 本発明の循環式接触曝気法に鉄接触濾材を用いる方法
は,プラスチック濾材のみではリン除去効果がほとんど
得られないにもかかわらず飛躍的に向上するリン除去効
率が得られるとともに接触濾材を一度設置すれば,たと
え経日とともに濾材表面に微生物膜が肥厚化しても取外
しすることなくそのままで洗浄が可能であり,簡単に接
触濾材に汚水を循環曝気するのみで長期間にわたる脱リ
ン効果が高効率で持続して得られ,発生汚泥量も極めて
すくないという優れた汚水処理方法である。また,本発
明によって得られる汚泥は,リン酸鉄を主成分とする有
機汚泥であるので,農作物の肥料として好適に用いるこ
とができる。
(Effects of the Invention) The method of using the iron contact filter medium in the circulating contact aeration method of the present invention achieves a dramatic improvement in phosphorus removal efficiency while the phosphorus removal effect is hardly obtained only by the plastic filter medium. Once the contact filter medium is installed, even if the microbial film becomes thicker on the surface of the filter medium over time, it can be washed as it is without removing it, and it is easy to circulate and aerate the contact filter medium for long-term desorption. This is an excellent sewage treatment method in which the phosphorus effect is highly efficient and sustained, and the amount of sludge generated is extremely small. Moreover, since the sludge obtained by the present invention is an organic sludge containing iron phosphate as a main component, it can be suitably used as a fertilizer for agricultural crops.

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

第1図は本発明の方法に用いる循環式接触曝気処理装置
の概略縦断面図,第2図は鉄接触濾材表面積に対するリ
ン負荷(g/m2・日)の変化によって得られる汚水中の
リンの除去率の実験値を示すリン負荷とリン除去率との
相関図である。 1……汚水導入管,2……接触濾材槽,3……隔壁,4
……曝気室,5……散気管,6……接触濾材,7……処
理水排出口,8……逆洗管
FIG. 1 is a schematic vertical sectional view of a circulating contact aeration treatment apparatus used in the method of the present invention, and FIG. 2 is phosphorus in wastewater obtained by changing phosphorus load (g / m 2 · day) with respect to iron contact filter medium surface area. FIG. 3 is a correlation diagram showing the phosphorus removal rate and the phosphorus loading showing the experimental value of the removal rate. 1 ... sewage introduction pipe, 2 ... contact filter media tank, 3 ... division wall, 4
…… Aeration chamber, 5 …… Diffuser, 6 …… Contact filter, 7 …… Treated water outlet, 8 …… Backwash pipe

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】接触濾材として鉄濾材の単独又はこれを主
材に充填し、該鉄濾材の表面積に対するリンの負荷が
1.0g/m2・日以下になるように汚水を循環曝気処理
して汚水中の有機物とリンを除去することを特徴とする
汚水の処理方法。
1. An iron filter medium as a contact filter medium or a main filter medium filled with the filter medium, and sewage is circulated and aerated so that the phosphorus load on the surface area of the iron filter medium is 1.0 g / m 2 · day or less. A method for treating sewage, which comprises removing organic matter and phosphorus in the sewage.
JP60019139A 1985-02-01 1985-02-01 Sewage treatment method Expired - Lifetime JPH0611440B2 (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP60019139A JPH0611440B2 (en) 1985-02-01 1985-02-01 Sewage treatment method
KR1019860000615A KR860006403A (en) 1985-02-01 1986-01-30 Sewage Treatment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60019139A JPH0611440B2 (en) 1985-02-01 1985-02-01 Sewage treatment method

Publications (2)

Publication Number Publication Date
JPS61178092A JPS61178092A (en) 1986-08-09
JPH0611440B2 true JPH0611440B2 (en) 1994-02-16

Family

ID=11991117

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60019139A Expired - Lifetime JPH0611440B2 (en) 1985-02-01 1985-02-01 Sewage treatment method

Country Status (2)

Country Link
JP (1) JPH0611440B2 (en)
KR (1) KR860006403A (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62279888A (en) * 1986-05-28 1987-12-04 Kobe Chutetsusho:Kk Treatment of sewage
JPS63111998A (en) * 1986-10-29 1988-05-17 Res Dev Corp Of Japan Sewage treatment and device therefor
JPS63168100U (en) * 1987-04-22 1988-11-01
JPH057397U (en) * 1991-02-05 1993-02-02 株式会社西原環境衛生研究所 Contact aeration sewage treatment equipment
JPH0767558B2 (en) * 1993-03-08 1995-07-26 虹技株式会社 Sewage treatment method
JP2008272711A (en) * 2007-05-07 2008-11-13 Itsuo Morizaki Water clarification method and clarification apparatus

Also Published As

Publication number Publication date
KR860006403A (en) 1986-09-11
JPS61178092A (en) 1986-08-09

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