JPS63158195A - Treatment of sewage - Google Patents

Treatment of sewage

Info

Publication number
JPS63158195A
JPS63158195A JP61305676A JP30567686A JPS63158195A JP S63158195 A JPS63158195 A JP S63158195A JP 61305676 A JP61305676 A JP 61305676A JP 30567686 A JP30567686 A JP 30567686A JP S63158195 A JPS63158195 A JP S63158195A
Authority
JP
Japan
Prior art keywords
carrier
treatment
sewage
treatment tank
fluidized bed
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
JP61305676A
Other languages
Japanese (ja)
Inventor
Yuji Yoshii
吉井 裕二
Tatsuo Takechi
武智 辰夫
Hideji Takeuchi
竹内 秀二
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.)
JFE Engineering Corp
Original Assignee
NKK Corp
Nippon Kokan 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 NKK Corp, Nippon Kokan Ltd filed Critical NKK Corp
Priority to JP61305676A priority Critical patent/JPS63158195A/en
Publication of JPS63158195A publication Critical patent/JPS63158195A/en
Pending legal-status Critical Current

Links

Classifications

    • 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

Abstract

PURPOSE:To treat sewage at low cost, by treating the sewage using powdery coke as a carrier. CONSTITUTION:A treatment tank 3 is packed with a carrier composed of powdery coke. Subsequently, raw sewage 1 is introduced into the treatment tank 3 by a raw water pump 2 and, at the same time, air is blown in the distribution cylinder 4 arranged in the treatment tank 3 from a blower 5. The carrier 6 in the treatment tank 3 is allowed to rise in the distribution cylinder 4 by air lift action and subsequently allowed to fall in the treatment tank 3 outside the distribution cylinder to be smoothly fluidized and recirculated. After the biological oxidation treatment, the carrier 6 is separated by the carrier separation part 7 provided to the upper part of the treatment tank 3 and treated water 8 is allowed to overflow from the separation part 7. By this method, sewage can be satisfactorily purified at low running cost.

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は、下水、各種産業廃水、生活用水等の汚水の処
理方法に関し、特に微生物を付着させた担体を用いる汚
水処理方法の改良に係わる。
[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to a method for treating wastewater such as sewage, various industrial wastewater, and domestic water, and particularly relates to an improvement in a method for treating wastewater using a carrier to which microorganisms are attached. .

[従来の技術] 汚水処理方法の一つとして、担体を処理槽内に流動状態
に保持し、該担体に付着した微生物の作用により該処理
槽内に供給した汚水を浄化させる流動床式処理方法が知
られている。こうした流動床式汚水処理方法としては、
以下に説明する好気流動床式処理方法と、嫌気流動床式
処理方法とがある。
[Prior Art] As one of the sewage treatment methods, there is a fluidized bed treatment method in which a carrier is kept in a fluidized state in a treatment tank and the sewage supplied into the treatment tank is purified by the action of microorganisms attached to the carrier. It has been known. These fluidized bed sewage treatment methods include:
There are an aerobic fluidized bed treatment method and an anaerobic fluidized bed treatment method, which will be explained below.

好気流動床式処理は、第1図に示すように原汚水lを原
水ポンプ2により処理槽3内に導入する。
In the aerobic fluidized bed treatment, as shown in FIG. 1, raw sewage l is introduced into a treatment tank 3 by a raw water pump 2.

同時に、処理槽3内に配置した整流gJ4内に曝気用ブ
ロアー5からエアーを吹込み、処理槽3内の担体6をエ
アーリフト作用により整流筒4内を上昇させた後、整流
筒4外側の処理槽3内を下降させて担体6を円滑に流動
、循環させる。こうした操作により、原汚水は処理槽3
内で流動状態に保持された担体6に付着・繁殖された好
気性微生物により生物酸化処理された後、処理槽3上部
の担体分離7から処理水8としてオーバーフローする。
At the same time, air is blown from the aeration blower 5 into the rectifier gJ4 arranged in the treatment tank 3, and after the carrier 6 in the treatment tank 3 is raised inside the rectifier cylinder 4 by the air lift action, The inside of the processing tank 3 is lowered to smoothly flow and circulate the carrier 6. Through these operations, the raw sewage is transferred to the treatment tank 3.
After being subjected to biological oxidation treatment by aerobic microorganisms attached and propagated on the carrier 6 which is kept in a fluid state within the tank, it overflows as treated water 8 from the carrier separator 7 at the upper part of the treatment tank 3.

この担体分離部7においては、循環する担体Bが処理水
8と共に処理槽3外に流出するのを防止する作用をなし
ている。
This carrier separation section 7 functions to prevent the circulating carrier B from flowing out of the treatment tank 3 together with the treated water 8.

嫌気流動床式処理は、第2図に示すように原汚水lを原
水ポンプ2により処理槽3内に導入し、該処理Vaa内
番内勤流動担体6に付着・繁殖された嫌気性微生゛物に
より原汚水が嫌気的生物処理され、処理水8として排出
する方法である。この場合、担体6の流動は処理水8の
一部を循環液9として循環ポンプ10により処理槽3下
部より導入することによりなされる。
In the anaerobic fluidized bed treatment, as shown in FIG. In this method, raw wastewater is subjected to anaerobic biological treatment using a substance and then discharged as treated water 8. In this case, the flow of the carrier 6 is achieved by introducing a part of the treated water 8 as a circulating liquid 9 from the lower part of the treatment tank 3 using a circulation pump 10.

ところで、上記流動床式汚水処理方法に用いる担体とし
ては、従来より砂又は活性炭からなるものを使用してい
る。
Incidentally, the carrier used in the fluidized bed sewage treatment method has conventionally been made of sand or activated carbon.

[発明が解決しようとする問題点] しかしながら、従来の砂又は活性炭を担体として用いる
汚水処理方法では次のような問題があ′った。
[Problems to be Solved by the Invention] However, conventional sewage treatment methods using sand or activated carbon as carriers have had the following problems.

■9担体に活性炭を用いる場合には、その製造原料や製
造技術等により価格が高価となるため、汚水処理コスト
の高騰化を招く。
(9) When activated carbon is used as a carrier, it is expensive due to its manufacturing raw materials and manufacturing technology, leading to an increase in wastewater treatment costs.

■、担体に砂を用いる場合には、価格はそれ程問題にな
らないが、比重が2.6と大きいため、その流動化に多
大なエネルギーを必要として汚水処理コストの高騰化の
要因となる。
(2) When sand is used as a carrier, the price is not so much of an issue, but since the specific gravity is as high as 2.6, a large amount of energy is required to fluidize it, which causes an increase in wastewater treatment costs.

■、また、担体に砂を用いる場合には担体に微生物が付
着して見掛は比重が小さくなった際、処理槽上部の担体
分離部で処理水から砂を分離しきれず、処理水と共に砂
が外部に流出する可能性がある。このような場合には、
担体は余剰汚泥と共に汚泥処理工程へ導入されるが、砂
は不燃性のために焼却処理を施しても残渣となり、不要
な産業廃棄物となる。
■Also, when sand is used as a carrier, when microorganisms adhere to the carrier and the apparent specific gravity becomes small, the carrier separation section at the top of the treatment tank cannot completely separate the sand from the treated water, resulting in sand being mixed with the treated water. may leak outside. In such a case,
The carrier is introduced into the sludge treatment process together with excess sludge, but since sand is nonflammable, even if it is incinerated, it remains as a residue and becomes unnecessary industrial waste.

なお、前記■と■の問題に関しては生物付着担体を用い
る流動床式汚水処理方法のみならず、固定床式汚水処理
方法におても共通した問題である。
The above-mentioned problems (1) and (2) are common not only to fluidized bed sewage treatment methods using biofouling carriers, but also to fixed bed sewage treatment methods.

本発明は、上記従来の問題点を解決するためになされた
もので、低コストの担体で、かつ低ランニングコストで
汚水を処理し得る方法を提供するものである。
The present invention was made to solve the above-mentioned conventional problems, and provides a method for treating wastewater using a low-cost carrier and at low running costs.

[問題点を解決するための手段] 本発明は、担体に付着した微生物の作用により汚水を浄
化する汚水処理方法において、前記担体として粉状コー
クスを用いることを特徴とする汚水処理方法である。
[Means for Solving the Problems] The present invention is a sewage treatment method for purifying sewage by the action of microorganisms attached to a carrier, which is characterized in that powdered coke is used as the carrier.

式消火設備又′はコ″−クス湿式消火設備で発生したそ
のもの、或いはコークスを粉状に粉砕したもの等を使用
できる。
Coke generated in wet extinguishing equipment or coke, or coke pulverized into powder, etc. can be used.

[作用コ しかして、本発明において担体として使用する粉状コー
クスは比表面積が例えば20〜5011L2/gである
ため、充分な量の微生物を付着でき1.汚水を良好に微
生物処理することができる。また、粉状コニクスは活性
炭に比べて著しく安価であり、しかも比重が例えば1.
8〜1.9と砂に在べて低いため、流動床式汚水処理に
適用した場合、流動化が容易となる。更に、粉状コーク
スを流動床汚水処理に適用した場合、担体に微生物が付
着して見掛は比重が小さくなった際に担体分離部で担体
を分離しきれずに単体が処理水と共に外部に流出するこ
とがある。この場合、前記流出担体は余剰汚泥と共に汚
泥処理工程へ導入され、濃縮→嫌気性消化−説水−焼却
等の処理を受けるが、担体として用いる粉状コークスは
炭素を含んだ固体燃料として働くため、焼却工程におい
て自燃することができ、不要な産業廃棄物として煩わし
い処理を考慮する必要がなくなる。従って、低コストの
担体で、かつ低ランニングコストで汚水を良好に浄化で
きる。
[Function] However, since the powdered coke used as a carrier in the present invention has a specific surface area of, for example, 20 to 5011 L2/g, it is possible to attach a sufficient amount of microorganisms.1. Sewage can be effectively treated with microorganisms. In addition, powdered conics is significantly cheaper than activated carbon, and has a specific gravity of, for example, 1.
8 to 1.9, which is lower than that of sand, making it easy to fluidize when applied to fluidized bed sewage treatment. Furthermore, when powdered coke is applied to fluidized bed sewage treatment, when microorganisms adhere to the carrier and the apparent specific gravity becomes smaller, the carrier cannot be completely separated in the carrier separation section and the coke itself flows out together with the treated water. There are things to do. In this case, the effluent carrier is introduced into the sludge treatment process together with excess sludge, and undergoes treatments such as concentration, anaerobic digestion, clarification, and incineration, but the powdered coke used as the carrier acts as a solid fuel containing carbon. , it can self-combust during the incineration process, eliminating the need to consider cumbersome treatment as unnecessary industrial waste. Therefore, wastewater can be effectively purified using a low-cost carrier and at low running costs.

[発明の実施例] 以下、本発明の実施例を前述した第1図及び第2図を参
照して詳細に説明する。
[Embodiments of the Invention] Hereinafter, embodiments of the present invention will be described in detail with reference to FIGS. 1 and 2 described above.

実施例1 まず、第1図に示すように処理槽3内に粉状コークスか
らなる担体を充填した。つづいて、原汚水lを原水ポン
プ2により処理槽3内に導入した。
Example 1 First, as shown in FIG. 1, a carrier made of powdered coke was filled into the treatment tank 3. Subsequently, raw sewage l was introduced into the treatment tank 3 by the raw water pump 2.

同時に、処理槽3内に配置した整流筒4内にブロアー5
からエアーを吹込み、処理槽3内の担体6をエアーリフ
ト作用により整流筒4内を上昇させた後、整流筒4外側
の処理t’63内を下降させて担体Gを円滑に流動、循
環させた。こうした操作により、原汚水は処理槽3内で
流動状態に保持された担体6に付着・繁殖された好気性
微生物により生物酸化処理された後、処理槽3上部の担
体分離部7により担体6を分離し、該分離部7から処理
水8をオーバーフローさせた。
At the same time, a blower 5 is installed in the rectifier cylinder 4 arranged in the processing tank 3.
Air is blown into the treatment tank 3 to raise the carriers 6 inside the rectifying cylinder 4 by air lift action, and then lowering the inside of the treatment t'63 outside the rectifying cylinder 4 to smoothly flow and circulate the carriers G. I let it happen. Through these operations, the raw sewage is subjected to biological oxidation treatment by aerobic microorganisms attached and bred on the carrier 6 kept in a fluid state in the treatment tank 3, and then the carrier 6 is removed by the carrier separation section 7 at the upper part of the treatment tank 3. The treated water 8 was allowed to overflow from the separation section 7.

上記汚水処理に際し、次のような条件に設定した。The following conditions were set for the above wastewater treatment.

処理槽3;有効容ff150ノ(流動部容i!25i、
担体分離部容量25))、担体分離部の直径40011
%流動部の直径200zi。
Processing tank 3: Effective volume ff150 (flowing section volume i!25i,
Capacity of carrier separating section 25)), Diameter of carrier separating section 40011
% Diameter of flow section 200zi.

整流筒4;直径140zm、高さ1000F!1a。Rectifier cylinder 4; diameter 140zm, height 1000F! 1a.

担体としての粉状コークス;、コークス乾式消火設備の
サイクロンから回収した下記第1表に示す成分、下記第
2表に示す粒度分布を持ち、かつ比重が1.8〜1.9
、比表面積が20〜50m2/gのものを用い、処理槽
3内に5.0ノ充填した。
Powdered coke as a carrier; components shown in Table 1 below recovered from the cyclone of coke dry extinguishing equipment, having a particle size distribution shown in Table 2 below, and a specific gravity of 1.8 to 1.9
, a specific surface area of 20 to 50 m2/g was used, and 5.0 m2/g was filled into the processing tank 3.

比較例1 担体として有効径0.11m、均等係数1.8、比重2
.6の砂を使用した以外、実施例1と同様な好気流動床
汚水処理を行なった。
Comparative Example 1 Effective diameter of carrier: 0.11 m, uniformity coefficient: 1.8, specific gravity: 2
.. The same aerobic fluidized bed sewage treatment as in Example 1 was carried out except that No. 6 sand was used.

しかして、本実施例1及び比較例1における担体を流動
化するに必要な曝気用ブロアー5からのエアー量を測定
した。その結果、本実施例1の粉状コークスの場合は8
ノ/1n1比較例1の砂の場合は5(lj’ / 1n
となり、比較例1に比べて約l/6のエアー量で担体を
流動化することが可能であることが確認された。
Thus, the amount of air from the aeration blower 5 required to fluidize the carrier in Example 1 and Comparative Example 1 was measured. As a result, in the case of powdered coke of Example 1, 8
/1n1 In the case of the sand of Comparative Example 1, it is 5(lj' / 1n
Therefore, it was confirmed that it was possible to fluidize the carrier with an amount of air about 1/6 compared to Comparative Example 1.

第1表 第2表 実施例2 まず、第2図に示すように処理槽3内に粉状コークスか
らなる担体を充填した。つづいて、原汚水lを原水ポン
プ2によりの処理槽3内に導入し、同時に処理水8の一
部を循環液9として循環ポンプlOにより処理槽3下部
より導入し、処理槽3内の担体6を流動させ、該担体6
に付着会繁殖された嫌気性微生物により原汚水を嫌気的
生物処理し、処理水8を処理槽3上部から排出すると共
に、一部を循環液9として使用した。
Table 1 Table 2 Example 2 First, as shown in FIG. 2, a carrier made of powdered coke was filled into the treatment tank 3. Next, the raw sewage l is introduced into the treatment tank 3 by the raw water pump 2, and at the same time, a part of the treated water 8 is introduced from the lower part of the treatment tank 3 by the circulation pump lO as the circulating liquid 9, and the carrier in the treatment tank 3 is 6 is made to flow, and the carrier 6
Raw sewage was subjected to anaerobic biological treatment using anaerobic microorganisms grown in adhesion, and treated water 8 was discharged from the upper part of treatment tank 3, and a portion was used as circulating fluid 9.

上記汚水処理に際し、次のような条件に設定した。The following conditions were set for the above wastewater treatment.

処理槽3;有効容量28)、直径20011%   。Processing tank 3; effective capacity 28), diameter 20011%.

高さ1000B。Height: 1000B.

担体としての粉状コークス;、実施例1と同様な諸性質
を有するものを処理槽3内に11.0ノ充填した。
Powdered coke as a carrier having the same properties as in Example 1 was filled into the treatment tank 3 in an amount of 11.0 μm.

比較例2 担体として有効径0.11jIJl、均等係数1.8、
比重2.6の砂を使用した以外、実施例2と同様な嫌気
流動床汚水処理を行なった。
Comparative Example 2 As a carrier, the effective diameter is 0.11jIJl, the uniformity coefficient is 1.8,
Anaerobic fluidized bed sewage treatment was carried out in the same manner as in Example 2, except that sand with a specific gravity of 2.6 was used.

しかして、本実施例2及び比較例2における担体膨張率
50%を得るのに必要な循環水ff1(線速度)を調べ
た。その結果、本実施例2の粉状コークスの場合は3.
8771/hr、比較例2の砂の場合は15.3m/h
rとなり、比較例2に比べて約1/4の線速度で担体を
流動化することが可能であることが確認された。
Therefore, the circulating water ff1 (linear velocity) necessary to obtain a carrier expansion rate of 50% in Example 2 and Comparative Example 2 was investigated. As a result, in the case of the powdered coke of Example 2, 3.
8771/hr, 15.3 m/hr for sand of Comparative Example 2
r, and it was confirmed that it was possible to fluidize the carrier at a linear velocity of about 1/4 compared to Comparative Example 2.

実施例3 第1図の汚水処理装置、第2図の汚水処理装置を用いて
都市下水の処理実験を行なった。第1図の好気流動床式
汚水処理では、実施例1と同様な粉状コークスを処理槽
3に5.0ノ充填し、下記第3表に示す性状の原水を流
9300 、ff /da’/で処理槽3に導入し、エ
アー量は8.ff/ff1inとした。第2図の嫌気流
動床式汚水処理では、実施例1と同様な粉状コークスを
処理槽3に11. 、i?充填し、同様な性状の原水を
fLQ 9(D’ / dayで処理槽3に導入し、循
環流量は2.0 、ff/minとした。その結果を、
同第3表に併記した。
Example 3 An urban sewage treatment experiment was conducted using the sewage treatment apparatus shown in FIG. 1 and the sewage treatment apparatus shown in FIG. 2. In the aerobic fluidized bed sewage treatment shown in Fig. 1, the treatment tank 3 was filled with 5.0 kg of powdered coke similar to that in Example 1, and the raw water having the properties shown in Table 3 below was flowed at 9300 ff/da. ' / is introduced into the processing tank 3, and the air amount is 8. ff/ff1in. In the anaerobic fluidized bed sewage treatment shown in FIG. ,i? The raw water with similar properties was introduced into the treatment tank 3 at fLQ 9 (D'/day), and the circulation flow rate was 2.0, ff/min.The results were as follows:
It is also listed in Table 3.

第3表 上記第3表から明らかなように担体として粉状コークス
を用いることによって好気流動床式汚水処理及び嫌気流
動床式汚水処理のいずれの場合でもBOD%CODを良
好に除去できることがわかる。また、好気流動床式汚水
処理においては硝化処理についても優れた成績が得られ
ることがわかる。
Table 3 As is clear from Table 3 above, it can be seen that by using powdered coke as a carrier, BOD% COD can be removed well in both aerobic fluidized bed sewage treatment and anaerobic fluidized bed sewage treatment. . Furthermore, it can be seen that excellent results can be obtained in nitrification treatment in aerobic fluidized bed wastewater treatment.

なお、上記実施例では流動床式汚水処理につい・て説明
したが、固定床式汚水処理に適用しても同様な効果を発
揮できる。
In addition, although the above-mentioned example explained the fluidized bed type sewage treatment, the same effect can be exhibited even if it is applied to the fixed bed type sewage treatment.

[発明の効果] 以上詳述した如く、本発明によれば低コストの担体で、
かつ低ランニングコストで汚水を良好に浄化し得る汚水
処理方法を提供できる。
[Effects of the Invention] As detailed above, according to the present invention, a low-cost carrier,
Moreover, it is possible to provide a sewage treatment method that can purify sewage well at low running costs.

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

第1図は、好気流動床式汚水処理装置を示す概略図、第
2図は、嫌気流動床式汚水処理装置を示す概略図で返る
。 l・・・原汚水、2・・・原水ポンプ、3・・・処理槽
、4・・・整流筒、5・・・曝気用ブロアー、6・・・
担体、7・・・担体分離部、8・・・処理水、9・・・
循環水、lO・・・循環ポンプ。 出願人代理人 弁理士 鈴江武彦 第 1 レフ 篇2 X 手続補正書 昭和  住3.2月−2日
FIG. 1 is a schematic diagram showing an aerobic fluidized bed type sewage treatment device, and FIG. 2 is a schematic diagram showing an anaerobic fluidized bed type sewage treatment device. l... Raw sewage, 2... Raw water pump, 3... Treatment tank, 4... Rectifier cylinder, 5... Aeration blower, 6...
Carrier, 7... Carrier separation section, 8... Treated water, 9...
Circulating water, lO...circulation pump. Applicant's agent Patent attorney Takehiko Suzue No. 1 Ref. 2

Claims (1)

【特許請求の範囲】[Claims] 担体に付着した微生物の作用により汚水を浄化する汚水
処理方法において、前記担体として粉状コークスを用い
ることを特徴とする汚水処理方法。
A sewage treatment method for purifying sewage by the action of microorganisms attached to a carrier, characterized in that powdered coke is used as the carrier.
JP61305676A 1986-12-22 1986-12-22 Treatment of sewage Pending JPS63158195A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61305676A JPS63158195A (en) 1986-12-22 1986-12-22 Treatment of sewage

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61305676A JPS63158195A (en) 1986-12-22 1986-12-22 Treatment of sewage

Publications (1)

Publication Number Publication Date
JPS63158195A true JPS63158195A (en) 1988-07-01

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Family Applications (1)

Application Number Title Priority Date Filing Date
JP61305676A Pending JPS63158195A (en) 1986-12-22 1986-12-22 Treatment of sewage

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JP (1) JPS63158195A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2011212513A (en) * 2010-03-31 2011-10-27 Mitsui Eng & Shipbuild Co Ltd Microbial treatment system
JP2014042883A (en) * 2012-08-27 2014-03-13 Swing Corp Operational method of biological membrane treatment device
JP2019202254A (en) * 2018-05-22 2019-11-28 壽環境機材株式会社 Waste water treatment equipment and waste water treatment method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2011212513A (en) * 2010-03-31 2011-10-27 Mitsui Eng & Shipbuild Co Ltd Microbial treatment system
JP2014042883A (en) * 2012-08-27 2014-03-13 Swing Corp Operational method of biological membrane treatment device
JP2019202254A (en) * 2018-05-22 2019-11-28 壽環境機材株式会社 Waste water treatment equipment and waste water treatment method

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