JP2002336604A - Method and apparatus for separating pollutants in polluted water - Google Patents

Method and apparatus for separating pollutants in polluted water

Info

Publication number
JP2002336604A
JP2002336604A JP2001143647A JP2001143647A JP2002336604A JP 2002336604 A JP2002336604 A JP 2002336604A JP 2001143647 A JP2001143647 A JP 2001143647A JP 2001143647 A JP2001143647 A JP 2001143647A JP 2002336604 A JP2002336604 A JP 2002336604A
Authority
JP
Japan
Prior art keywords
contaminated water
water
stirring
contaminants
upstream
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
JP2001143647A
Other languages
Japanese (ja)
Other versions
JP3920591B2 (en
Inventor
Sumio Hosokawa
澄男 細川
Tetsuya Takatsu
哲也 高津
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.)
ROKKO KAIHATSU KK
Original Assignee
ROKKO KAIHATSU 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 ROKKO KAIHATSU KK filed Critical ROKKO KAIHATSU KK
Priority to JP2001143647A priority Critical patent/JP3920591B2/en
Priority to TW091108416A priority patent/TWI290911B/en
Priority to KR1020020025758A priority patent/KR100697394B1/en
Priority to CNB021193509A priority patent/CN1233574C/en
Publication of JP2002336604A publication Critical patent/JP2002336604A/en
Application granted granted Critical
Publication of JP3920591B2 publication Critical patent/JP3920591B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01FMIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F25/00Flow mixers; Mixers for falling materials, e.g. solid particles
    • 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
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment

Abstract

PROBLEM TO BE SOLVED: To provide a separating method and a separating apparatus for rapidly separating pollutants in a large quantity of the abrasive polluted water. SOLUTION: The pollutants in the polluted water are flocculated and separated by passing the polluted water successively from the upstream side to the downstream side while stirring in stirring tanks 31-37, incorporating a plurality of kinds of flocculants in the polluted water by one kind with a certain time difference successively from the upstream to the downstream while stirring to finish the incorporation of full kinds of the flocculants at the downmost stream position.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、例えば、産業排
水、生活排水、池、河川、下水道等の汚濁水に含まれる
汚濁物を分離する方法及びその装置に関する。
The present invention relates to a method and an apparatus for separating pollutants contained in polluted water such as industrial wastewater, domestic wastewater, ponds, rivers, and sewers.

【0002】[0002]

【従来背景】産業排水、生活排水、池、河川、下水道等
の汚濁水には、環境に悪影響を与える汚濁物(有毒物
質、ヘドロ、汚泥、食物かす等)が多く含まれている。
例えば、産業排水における光学系部品の研磨剤汚濁水で
は、遷移金属元素や希土類元素等の有毒な微粒子を含ん
でいるため、研磨後に廃棄する場合には有毒物質である
研磨剤及び研磨くずを液体と分離する必要がある。現
在、汚濁水は、沈殿槽において汚濁物を自然に沈殿させ
て液体と分離させているが、この方法では、完全沈殿ま
で相当の時間を要する上に、大量の汚濁水を処理するた
めには沈殿槽の規模を大きくする必要があり、時間的に
も設備的にも多大なコストを要している。
BACKGROUND ART Polluted water such as industrial wastewater, domestic wastewater, ponds, rivers, sewers, etc., contains a lot of pollutants (toxic substances, sludge, sludge, food waste, etc.) which adversely affect the environment.
For example, abrasive polluted water of optical components in industrial wastewater contains toxic fine particles such as transition metal elements and rare earth elements. And need to be separated. At present, polluted water naturally precipitates pollutants in a sedimentation tank and separates it from liquid.However, this method requires a considerable amount of time to complete settling, and requires a large amount of polluted water to be treated. It is necessary to increase the size of the sedimentation tank, which requires a great deal of time and equipment.

【0003】又、最近では、汚濁水に凝集剤を混入攪拌
して汚濁物を凝集することによって、沈殿時間を短縮す
る方法が試みられているが、この方法にしても大量の汚
濁水を処理するためには規模の大きい沈殿槽が必要であ
るし、沈殿槽内の汚濁水を平均して攪拌可能とする攪拌
装置を用意する必要があり、大量の汚濁水処理にという
課題を解決できるものではない。
Recently, a method of shortening the settling time by mixing a flocculant into the polluted water and stirring to condense the pollutant has been attempted. However, even with this method, a large amount of the polluted water is treated. To do so, a large-scale sedimentation tank is required, and it is necessary to prepare a stirrer that can stir the contaminated water in the sedimentation tank on average, which can solve the problem of treating large amounts of contaminated water. is not.

【0004】[0004]

【発明が解決しようとする課題】そこで、本発明は、汚
濁水に含まれる汚濁物を迅速、且つ、大量に分離処理す
ることを課題とし、この課題を解決できる分離方法と分
離装置の提供を目的とする。
SUMMARY OF THE INVENTION Accordingly, an object of the present invention is to provide a method and apparatus for separating a large amount of contaminants contained in contaminated water quickly and in large quantities. Aim.

【0005】[0005]

【課題を解決するための手段】上記した目的を達成する
ために本発明が採用した技術的手段は、汚濁物を含んだ
汚濁水を、上流から下流へ流しながら水流によってに攪
拌し、その道中において、前記汚濁水に複数種の凝集剤
を、上流から下流に順次時間差を持って1種類毎に混入
し、汚濁水と攪拌することによって、汚濁水中の汚濁物
を凝集して分離する方法である。(請求項1)
The technical means adopted by the present invention to achieve the above object is to agitate polluted water containing pollutants by flowing water while flowing from upstream to downstream. In the method of mixing a plurality of types of flocculants in the contaminated water, one by one from upstream to downstream sequentially with a time lag, by stirring with the contaminated water, a method for coagulating and separating contaminants in the contaminated water. is there. (Claim 1)

【0006】[0006]

【発明の実施の形態】又、上流から下流へ並列状に連通
する複数の攪拌槽に、汚濁物を含んだ汚濁水を上流から
下流へ順に流しながら水流により攪拌し、その道中にお
いて、前記攪拌槽内の汚濁水に複数種の凝集剤を、上流
の攪拌槽から下流の攪拌槽に順次時間差を持って1種類
毎に混入し、汚濁水と攪拌することによって、汚濁水中
の汚濁物を凝集して分離する方法とすることがより効果
的である。(請求項2)
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS In addition, a plurality of agitation tanks communicating in parallel from upstream to downstream are agitated by a water flow while flowing polluted water containing pollutants in order from upstream to downstream. Multiple types of flocculants are mixed into the contaminated water in the tank from the upstream agitation tank to the downstream agitation tank one by one with a time lag, and stirred with the contaminated water to coagulate the contaminants in the contaminated water. It is more effective to adopt a method of separating by performing the separation. (Claim 2)

【0007】汚濁物の分離を効果的に行い、又は、汚濁
物が分離した後の排水は、ph値が略7前後であること
が条件であるため、本発明では、汚濁水のphを調整す
るph調整剤を、最上流と最下流から汚濁水に混入し、
汚濁水と攪拌する方法を用いる。(請求項3)
In the present invention, the ph value of the polluted water is adjusted because the ph value of the waste water after the pollutant is effectively separated or the effluent after the separated pollutant is separated is about 7. Ph adjuster mixed into the polluted water from the uppermost stream and the lowermost stream,
A method of stirring with contaminated water is used. (Claim 3)

【0008】前記請求項1又は請求項2の方法を実施可
能な装置としては、汚濁物を含んだ汚濁水の配管道中に
沿って複数の攪拌槽が並列状に配置され、各攪拌槽の全
て、もしくは、選択された複数個に、汚濁水中の汚濁物
を凝集する複数種の凝集剤が、上流側から下流側へ順次
時間差を持って1種類毎に混入されるようにした分離装
置により達成できる。(請求項4)
[0008] As an apparatus capable of carrying out the method of claim 1 or 2, a plurality of stirring tanks are arranged in parallel along a piping path of polluted water containing pollutants. Alternatively, a plurality of selected coagulants, which coagulate contaminants in contaminated water, are sequentially mixed from the upstream side to the downstream side with a time difference from one to another by a separation device. it can. (Claim 4)

【0009】又、各攪拌槽の全て、もしくは、選択され
た複数個には、各攪拌槽の全て、もしくは、選択された
複数個には、1個の攪拌槽につき1個の貯蔵部が備えら
れ、各貯蔵部に汚濁水中の汚濁物を凝集する複数種の凝
集剤を1種類毎に交互に貯蔵し、これら凝集剤を上流側
から下流側へ順次時間差を持って1種類毎に攪拌槽に混
入させるようにした分離装置により達成できる。(請求
項5)
[0009] Further, all or a selected plurality of the stirring tanks are provided with one storage unit for each of the stirring tanks or a plurality of the selected stirring tanks. In each storage unit, a plurality of flocculants for flocculating pollutants in the polluted water are alternately stored for each kind, and these flocculants are sequentially stirred from the upstream side to the downstream side with a time lag for each kind. This can be achieved by a separation device adapted to be mixed into the water. (Claim 5)

【0010】請求項3の方法を実施可能な装置として
は、少なくとも最上流部及び最下流部に位置する攪拌層
に、汚濁水のphを調整するph調整剤を混入するよう
にした分離装置(請求項6)、又は、少なくとも最上流
部及び最下流部に位置する攪拌層に備えられた貯蔵部
に、汚濁水のphを調整するph調整剤を貯蔵し、該p
h調整剤を貯蔵部から攪拌槽に混入するようにした分離
装置(請求項7)により達成できる。
[0010] As a device capable of carrying out the method of claim 3, there is provided a separation device in which a ph adjusting agent for adjusting ph of contaminated water is mixed into at least the agitating layers located at the uppermost stream and the lowermost stream. Claim 6) Alternatively, a ph regulator for adjusting the pH of the contaminated water is stored in at least a storage section provided in the stirring layer located at the uppermost stream portion and the lowermost stream portion.
This can be achieved by a separation device (claim 7) in which the adjusting agent is mixed into the stirring tank from the storage unit.

【0011】本発明の攪拌槽における攪拌構造は、例え
ば、モーターを動力とするプロペラ状の攪拌羽根を用い
ることが可能であるが、装置の簡素化及び省エネルギ
ー、さらに、騒音の抑制という点において、攪拌槽内に
吹き出される汚濁水の水勢によって攪拌するものが好適
である。(請求項8)
As the stirring structure in the stirring tank of the present invention, for example, a propeller-like stirring blade driven by a motor can be used. However, in terms of simplification of the apparatus, energy saving and suppression of noise. What stirs by the power of the polluted water blown out into a stirring tank is suitable. (Claim 8)

【0012】[0012]

【実施例】以下、本発明の実施例を図に基づいて説明す
ると、図1は、分離装置Aを模式的に表す構成図であ
る。分離装置Aは、上流(図面上右側)から、汚濁水槽
1、ポンプ2、複数(図面上7個)の攪拌槽31〜3
7、汚濁物用の沈殿槽4、排水槽5の順で並び、ポンプ
2より下流へ並ぶ各部材は全てパイプ6によって連通し
ている。攪拌槽31,37には、ph調整剤用の貯蔵部
61,62が備えられており、ph調整剤がコンプレッ
サー38によってパイプ39を介して攪拌槽31,37
に流入するようにしてある。又、攪拌槽32,34,3
6には、凝集剤用の貯蔵部63〜65が備えられてお
り、夫々異なる3種類の凝集剤が貯蔵されると共に、凝
集剤がコンプレッサー38によってパイプ39を介して
攪拌槽32,34,36に流入するようにしてある。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described below with reference to the drawings. FIG. Separation device A includes a polluted water tank 1, a pump 2, and a plurality (seven in the drawing) of stirring tanks 31 to 3 from the upstream (right side in the drawing).
7, the sedimentation sedimentation tank 4 and the drainage tank 5 are arranged in this order, and all the members arranged downstream from the pump 2 are all connected by a pipe 6. The stirring tanks 31 and 37 are provided with storage units 61 and 62 for the ph adjusting agent, and the ph adjusting agent is supplied to the stirring tanks 31 and 37 by the compressor 38 through the pipe 39.
It is made to flow into. In addition, stirring tanks 32, 34, 3
6 is provided with storage units 63 to 65 for flocculants, in which three different flocculants are stored, respectively, and the flocculants are stirred by the compressor 38 through the pipes 39 through the pipes 39, 34, 36. It is made to flow into.

【0013】ここで、攪拌槽31〜37を説明すると、
攪拌槽31〜37は、上下方向に長い略円塔状、且つ、
中途部から下端に向けて先窄まり状にしたものである。
そして、上方の側面に上流からのパイプ6が配管され、
下端に下流へ向かうパイプ6が配管されている。攪拌槽
31〜37の攪拌構造は、ポンプ2から吸い上げられた
汚濁水を勢い良く攪拌槽31内に流入させ、その流入す
る水勢と、下端に向かう先窄まり状部とによって渦流を
発生させて汚濁水を攪拌し、さらに、攪拌された汚濁水
は連続して流入される汚濁水の水勢によって、攪拌槽3
1内の攪拌された汚濁水を攪拌槽32に勢い良く流入さ
せる。攪拌槽32に流入した汚濁水は、前記攪拌槽31
での攪拌と同様に攪拌され、攪拌槽31に連続して流入
される汚濁水の水勢によって、攪拌槽32以下、全ての
攪拌槽に連続して勢い良く流入させると共に、攪拌し、
沈殿槽4に排水される。
Here, the stirring tanks 31 to 37 will be described.
The stirring tanks 31 to 37 are substantially columnar in a vertically long direction, and
It is tapered from the middle to the lower end.
And the pipe 6 from the upstream is laid on the upper side surface,
At the lower end, a pipe 6 that goes downstream is provided. The stirring structure of the stirring tanks 31 to 37 causes the polluted water sucked up from the pump 2 to flow into the stirring tank 31 vigorously, and a vortex is generated by the flowing water and the tapered portion toward the lower end. The contaminated water is agitated, and the agitated contaminated water is further stirred by the water flow of the contaminated water.
The stirred polluted water in 1 is vigorously flown into the stirring tank 32. The polluted water flowing into the stirring tank 32 is
In the same manner as the stirring in the above, the water of the polluted water continuously flowing into the stirring tank 31 is continuously and vigorously flown into all the stirring tanks below the stirring tank 32, and is stirred.
It is drained to the sedimentation tank 4.

【0014】尚、図示は省略するが、例えば、攪拌槽内
に多量のプラスティック片を入れ、汚濁水とともに攪拌
し、渦流での攪拌に加えて、汚濁水内を渦流に伴って動
き回るプラスティック片の攪拌によって、汚濁水の攪拌
効果を高めることができる。又、プラスティック片を入
れる場合には、汚濁水とともに下流へ流されないよう
に、攪拌槽内にふるい状の仕切りを設けるとよい。
Although not shown in the drawings, for example, a large amount of plastic pieces are put in a stirring tank and stirred with the contaminated water. In addition to the vortex agitation, the plastic pieces moving around in the contaminated water with the vortex flow. By stirring, the effect of stirring the polluted water can be enhanced. In addition, when a plastic piece is put in, a sieve-like partition is preferably provided in the stirring tank so as not to flow down with the contaminated water.

【0015】次に、攪拌槽31,32,34,36,3
7と貯蔵部61〜65との配管構造を説明する。攪拌槽
31,32,34,36,37と貯蔵部61〜65と
は、前記したようにパイプ39によって配管されるが、
具体的に説明すると、貯蔵部61〜65の下端に配管さ
れたパイプ39は、攪拌層31,32,34,36,3
7に至る中途で二又に分かれ、分かれた夫々がパイプ6
よりも上方の攪拌槽31,32,34,36,37の側
面に配管してある。コンプレッサー38と貯蔵部61〜
65はエアパイプ40によって配管され、コンプレッサ
ー38がエアを貯蔵部61〜65に送ることによって、
貯蔵部61〜65内のph調整剤及び凝集剤を攪拌槽3
1,32,34,36,37に注入させるようにしてあ
る。コンプレッサー38は、時間調節可能、且つ、ポン
プ2の運転と連動するタイマ(図示せず)によって動作
制御されており、ポンプ2が作動すると一定間隔で動作
開始と動作停止を交互に繰り返すようにしてある。符号
41は、ph調整剤及び凝集剤の注入量調節器であり、
この注入量調節器を調節することによって、必要な一定
量のph調整剤及び凝集剤を注入するようにしてある。
図中7はドレンバルブ、8は汚濁物排出部、9は排水部
である。
Next, stirring tanks 31, 32, 34, 36, 3
The piping structure between the storage unit 7 and the storage units 61 to 65 will be described. The stirring tanks 31, 32, 34, 36, and 37 and the storage units 61 to 65 are connected by the pipe 39 as described above.
More specifically, the pipes 39 provided at the lower ends of the storage units 61 to 65 are provided with the stirring layers 31, 32, 34, 36, 3.
Split into two on the way to 7 and each split into a pipe 6
Pipes are provided on the side surfaces of the stirring tanks 31, 32, 34, 36, and 37 above. The compressor 38 and the storage units 61 to 61
65 is piped by the air pipe 40, and the compressor 38 sends air to the storage units 61 to 65,
The ph regulator and the flocculant in the storage units 61 to 65 are mixed with the stirring tank 3
1, 32, 34, 36, 37. The operation of the compressor 38 is controlled by a timer (not shown) which is adjustable in time and which is linked to the operation of the pump 2. When the pump 2 is operated, the operation is started and stopped alternately at regular intervals. is there. Reference numeral 41 is a regulator for the injection amount of the ph regulator and the flocculant,
By adjusting this injection amount controller, a required constant amount of a ph regulator and a flocculant is injected.
In the figure, 7 is a drain valve, 8 is a pollutant discharge section, and 9 is a drain section.

【0016】尚、分離装置については、例示した構造に
限定されるものではなく、例えば、攪拌槽の数を増やし
てもよい。又、ポンプの作動、ph調整剤及び凝集剤の
混入タイミングや補充及び注入量調整、排水処理等を、
コンピュータによる集中制御によって、全自動化するこ
とによって、無制限の連続作動を可能とすることができ
る。
The structure of the separation device is not limited to the illustrated structure. For example, the number of stirring tanks may be increased. In addition, the operation of the pump, the mixing timing of the ph regulator and the coagulant, the replenishment and the injection amount adjustment, the drainage treatment, etc.
Unlimited continuous operation can be made possible by centralized control by a computer and fully automated.

【0017】以下、前記した構成の分離装置Aを用いた
汚濁水と汚濁水中の汚濁物の分離処理を順を追って説明
する。 汚濁水槽1内の汚濁水をポンプ2によって攪拌槽3
1内に勢い良く流入させて汚濁水を攪拌すると共に、貯
蔵部61からph調整剤が一定量注入される。 攪拌槽31でph調節剤とともに攪拌された汚濁水
は、連続して流入される汚濁水によって攪拌槽32に流
入してさらに攪拌されると共に、貯蔵部63から第1の
凝集剤が一定量注入される。 攪拌槽32で凝集剤とともに攪拌された汚濁水は、
連続して流入される汚濁水によって攪拌槽33に流入し
てさらに攪拌される 攪拌層33で攪拌された汚濁水は、連続して流入さ
れる汚濁水によって攪拌槽34に流入してさらに攪拌さ
れると共に、貯蔵部64から第2の凝集剤が一定量注入
される。 攪拌槽34で凝集剤とともに攪拌された汚濁水は、
連続して流入される汚濁水によって攪拌槽35に流入し
てさらに攪拌される。 攪拌層35で攪拌された汚濁水は、連続して流入さ
れる汚濁水によって攪拌槽36に流入してさらに攪拌さ
れると共に、貯蔵部65から第3の凝集剤が一定量注入
される。 攪拌槽36で凝集剤とともに攪拌された汚濁水は、
連続して流入される汚濁水によって攪拌槽37に流入し
てさらに攪拌されると共に、貯蔵部62からph調整剤
が一定量注入され、そして沈殿槽4に排水される。〜
で攪拌、ph調整、凝集剤混入が行なわれた汚濁水
は、その道中で液体と汚濁物が徐々に分離し、沈殿槽4
に至る時には完全分離しており、その状態で排水されて
沈殿槽4に汚濁物が沈降する。 沈殿槽4では汚濁物が沈降することによって、清澄
化した液体のみが排水槽5に排水される。 以上によって、汚濁水中の汚濁物を分離することができ
る。
Hereinafter, the separation process of the contaminated water and the contaminants in the contaminated water using the separation apparatus A having the above-described configuration will be described step by step. The polluted water in the polluted water tank 1 is stirred by the pump 2 into the stirred tank 3.
1 and vigorously flow into the tank 1 to agitate the polluted water, and a certain amount of a ph regulator is injected from the storage unit 61. The contaminated water stirred with the ph regulator in the stirring tank 31 flows into the stirring tank 32 by the continuously flowing polluted water and is further stirred, and a certain amount of the first flocculant is injected from the storage unit 63. Is done. The contaminated water stirred with the flocculant in the stirring tank 32 is
The contaminated water flowing into the stirring tank 33 is further stirred by the continuously flowing polluted water. The contaminated water stirred by the stirring layer 33 is further fed into the stirring tank 34 by the continuously flowing polluted water and further stirred. At the same time, a predetermined amount of the second flocculant is injected from the storage unit 64. The contaminated water stirred with the flocculant in the stirring tank 34 is
The polluted water continuously flows into the stirring tank 35 to be further stirred. The contaminated water stirred by the stirring layer 35 flows into the stirring tank 36 by the continuously flowing contaminated water, is further stirred, and a certain amount of the third flocculant is injected from the storage unit 65. The polluted water stirred with the flocculant in the stirring tank 36 is
The contaminated water continuously flows into the stirring tank 37 to be further stirred, and a certain amount of the ph regulator is injected from the storage unit 62 and discharged to the sedimentation tank 4. ~
In the contaminated water, which has been stirred, adjusted for pH, and mixed with a flocculant, the liquid and contaminants are gradually separated in the way, and the sedimentation tank 4
Is completely separated at the time of reaching, the wastewater is drained in that state, and the contaminants settle in the sedimentation tank 4. In the sedimentation tank 4, only the clarified liquid is drained to the drainage tank 5 by the sedimentation of the contaminants. As described above, pollutants in the polluted water can be separated.

【0018】ph調整剤及び凝集剤が一定量注入される
とコンプレッサー38は一旦停止すし一定時間後再開す
るが、再開までの時間としては、連続して流入する全て
の汚濁水に平均して混入できると共に、ph値の調整及
び凝集剤の化学反応が効果的に行なわれる時間であり、
攪拌槽の大きさや攪拌槽の数によって調整する。
When a certain amount of the ph regulator and the flocculant is injected, the compressor 38 is temporarily stopped and restarted after a certain period of time. And the time during which the ph value adjustment and the coagulant chemical reaction are effectively performed,
Adjust according to the size of the stirring tank and the number of stirring tanks.

【0019】次に、下記の条件とする分離装置を用いて
分離実験を行った結果を示す。 攪拌槽:7個、ともに直径70mm、長さ200mm、先窄
まり状部を有し、プラスティック片を有する。 ph調整剤及び凝集剤用貯蔵部の位置:前記実施例と同
様。 汚濁水のph調整値:7 使用汚濁水:遷移金属元素や希土類元素等を主成分とす
る研磨剤及び研磨くずを含んだ研磨廃液 使用凝集剤: 第1凝集剤:ベントナイト溶液 第2凝集剤:硫酸バンド溶液 第3凝集剤:高分子凝集剤溶液 ph調整剤及び凝集剤の混入タイミング:30秒毎 凝集剤の混入量:汚濁水流量の概ね1% この分離実験によれば、本装置は概ね300l/hの処
理能力があることが認められた。この前記実験結果から
推測すると、攪拌層の数や大きさを増やすことによっ
て、時間当りでさらに多くの汚濁水を分離処理すること
ができると思われる。又、凝集剤も実験に用いたものに
限定されるものではなく、凝集効果を有するものであれ
ば使用することが可能である。尚、本実験では、研磨剤
廃液の他にも、他の産業排水、生活排水、池、河川、下
水道の汚濁水でも汚濁物を、研磨剤廃液と略同様に分離
することができることが認められている。
Next, the results of a separation experiment performed using a separation apparatus having the following conditions are shown. Stirring tank: 7 pieces, each having a diameter of 70 mm, a length of 200 mm, a tapered portion, and a plastic piece. Location of storage for ph regulator and flocculant: Same as in the previous example. Ph adjustment value of polluted water: 7 polluted water used: polishing slurry containing abrasives mainly containing transition metal elements and rare earth elements and polishing wastes used flocculant: first flocculant: bentonite solution second flocculant: Sulfuric acid band solution Third flocculant: Polymer flocculant solution Timing of mixing ph regulator and flocculant: Every 30 seconds Amount of flocculant mixed: approximately 1% of the flow rate of polluted water According to this separation experiment, this apparatus is generally used. A capacity of 300 l / h was observed. From the above experimental results, it is considered that more polluted water can be separated per hour by increasing the number and size of the stirring layers. Further, the flocculant is not limited to those used in the experiment, and any flocculant having a flocculant effect can be used. In this experiment, it was recognized that pollutants can be separated in almost the same manner as the abrasive waste liquid, not only from the abrasive waste liquid, but also from other industrial wastewater, domestic wastewater, pond, river, and sewer polluted water. ing.

【0020】[0020]

【発明の効果】本発明は以上説明した通り、汚濁水を連
続して流しながら、複数種の凝集剤を時間差を持って1
種類毎に混入攪拌して汚濁物を分離する方法及び装置で
あるので、従来のような大型の沈殿槽を用いることな
く、大量の汚濁水を迅速に分離処理することができる。
さらに、攪拌槽の並びや配管形態によって、装置全体の
大きさを小型化することができるので、場所を取らない
小型のものでありながら、大量の汚濁水を分離処理する
ことが可能となる。しかも、請求項8の発明によれば、
分離装置の簡素化及び省エネルギー、さらに、騒音の抑
制という点において効果的であって、運転コストの削減
や周辺環境の保全が可能となる。
As described above, according to the present invention, a plurality of types of coagulants are added with a time lag while continuously flowing polluted water.
Since it is a method and apparatus for mixing and stirring each type to separate contaminants, a large amount of contaminated water can be rapidly separated without using a large sedimentation tank as in the related art.
Furthermore, since the size of the whole apparatus can be reduced by the arrangement of the stirring tanks and the form of piping, it is possible to separate and treat a large amount of polluted water even though the apparatus is small and does not take up much space. Moreover, according to the invention of claim 8,
This is effective in terms of simplification and energy saving of the separation device and suppression of noise, and enables reduction of operation cost and preservation of the surrounding environment.

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

【図1】本発明の分離装置の一例を示す模式図。FIG. 1 is a schematic view showing an example of a separation device of the present invention.

【符号の説明】[Explanation of symbols]

A:分離装置 2:ポンプ 31〜37:攪拌槽 38:コンプレッサー 39:パイプ 40:エアパイプ 6:パイプ 61,62:貯蔵部(ph調整剤用) 63〜65:貯蔵部(調整剤用) A: Separation device 2: Pump 31-37: Stirring tank 38: Compressor 39: Pipe 40: Air pipe 6: Pipe 61, 62: Storage unit (for ph regulator) 63-65: Storage unit (for regulator)

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C02F 1/52 C02F 1/52 K Fターム(参考) 4D015 BA19 BA21 BA24 BA28 BB13 CA20 DA05 DA32 DB01 DC02 EA03 EA07 EA08 EA14 EA16 EA17 EA32 4G035 AB44 AC12 ────────────────────────────────────────────────── ─── of the front page continued (51) Int.Cl. 7 identification mark FI theme Court Bu (reference) C02F 1/52 C02F 1/52 K F-term (reference) 4D015 BA19 BA21 BA24 BA28 BB13 CA20 DA05 DA32 DB01 DC02 EA03 EA07 EA08 EA14 EA16 EA17 EA32 4G035 AB44 AC12

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】汚濁物を含んだ汚濁水を、上流から下流へ
流しながら水流によってに攪拌し、 その道中において、前記汚濁水に複数種の凝集剤を、上
流から下流に順次時間差を持って1種類毎に混入し、汚
濁水と攪拌することによって、 汚濁水中の汚濁物を凝集して分離する方法。
1. A method according to claim 1, wherein the contaminated water containing the contaminants is stirred by a water stream while flowing from upstream to downstream, and a plurality of coagulants are added to the contaminated water with a time lag sequentially from upstream to downstream. A method in which the contaminants in the contaminated water are agglomerated and separated by mixing each type and stirring with the contaminated water.
【請求項2】上流から下流へ並列状に連通する複数の攪
拌槽に、汚濁物を含んだ汚濁水を上流から下流へ順に流
しながら水流により攪拌し、 その道中において、前記攪拌槽内の汚濁水に複数種の凝
集剤を、上流の攪拌槽から下流の攪拌槽に順次時間差を
持って1種類毎に混入し、汚濁水と攪拌することによっ
て、 汚濁水中の汚濁物を凝集して分離する方法。
2. A method according to claim 1, wherein said plurality of agitation tanks communicating in parallel from upstream to downstream are stirred by a water flow while flowing contaminated water containing contaminants in order from upstream to downstream. Multiple types of flocculants are mixed into water one by one with a time lag from the upstream agitation tank to the downstream agitation tank, and are stirred with the contaminated water to coagulate and separate contaminants in the contaminated water. Method.
【請求項3】汚濁水のphを調整するph調整剤を、少
なくとも最上流及び最下流から汚濁水に混入し、汚濁水
と攪拌する請求項1又は請求項2に記載の方法。
3. The method according to claim 1, wherein a ph regulator for adjusting the pH of the contaminated water is mixed into the contaminated water at least from the uppermost stream and the lowermost stream and stirred with the contaminated water.
【請求項4】汚濁物を含んだ汚濁水の配管道中に沿って
複数の攪拌槽が並列状に配置され、 各攪拌槽の全て、もしくは、選択された複数個に、汚濁
水中の汚濁物を凝集する複数種の凝集剤が、上流側から
下流側へ順次時間差を持って1種類毎に混入されるよう
にすることによって、 汚濁水中の汚濁物を凝集して分離する装置。
4. A plurality of agitation tanks are arranged in parallel along the pipe path of the contaminated water containing the contaminants, and the contaminants in the contaminated water are supplied to all or selected plural of the agitation tanks. An apparatus for aggregating and separating contaminants in contaminated water by allowing a plurality of coagulants to coagulate to be mixed for each type with a time lag from upstream to downstream sequentially.
【請求項5】各攪拌槽の全て、もしくは、選択された複
数個には、1個の攪拌槽につき1個の貯蔵部が備えら
れ、 各貯蔵部に汚濁水中の汚濁物を凝集する複数種の凝集剤
を1種類毎に交互に貯蔵し、これら凝集剤を上流側から
下流側へ順次時間差を持って1種類毎に攪拌槽に混入さ
せるようにすることによって、 汚濁水中の汚濁物を凝集して分離する装置。
5. A stirrer or all or a plurality of selected stirrers are provided with one storage unit for each stirrer, and each storage unit is provided with a plurality of types of agglomerated contaminants in polluted water. The flocculants are stored alternately for each type, and these flocculants are mixed into the agitation tank one by one with a time lag from the upstream side to the downstream side in order to coagulate the contaminants in the contaminated water. Device to separate.
【請求項6】少なくとも最上流部及び最下流部に位置す
る攪拌層に、汚濁水のphを調整するph調整剤を混入
するようにしている請求項4、又は、請求項5に記載の
装置。
6. The apparatus according to claim 4, wherein a ph adjusting agent for adjusting the ph of the contaminated water is mixed into at least the stirring layers located at the uppermost stream and the lowermost stream. .
【請求項7】少なくとも最上流部及び最下流部に位置す
る攪拌層に備えられた貯蔵部に、汚濁水のphを調整す
るph調整剤を貯蔵し、該ph調整剤を貯蔵部から攪拌
槽に混入するようにしている請求項5に記載の装置。
7. A ph adjuster for adjusting the pH of the contaminated water is stored in at least storage units provided in the agitating layers located at the uppermost stream and the lowermost stream. 6. The apparatus according to claim 5, wherein said apparatus is mixed with said apparatus.
【請求項8】攪拌槽が、攪拌槽内に吹き出される汚濁水
の水勢によって攪拌されるものである請求項4乃至請求
項7いずれか1項に記載の分離装置。
8. The separation apparatus according to claim 4, wherein the stirring tank is stirred by the power of polluted water blown into the stirring tank.
JP2001143647A 2001-05-14 2001-05-14 Method and apparatus for separating pollutants in polluted water Expired - Fee Related JP3920591B2 (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
JP2001143647A JP3920591B2 (en) 2001-05-14 2001-05-14 Method and apparatus for separating pollutants in polluted water
TW091108416A TWI290911B (en) 2001-05-14 2002-04-24 Method and apparatus for separating pollutants in polluted water
KR1020020025758A KR100697394B1 (en) 2001-05-14 2002-05-10 Process for separation of pollutant among polluted water and apparatus for the same
CNB021193509A CN1233574C (en) 2001-05-14 2002-05-13 Method for separating dirt from sewage and separator thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001143647A JP3920591B2 (en) 2001-05-14 2001-05-14 Method and apparatus for separating pollutants in polluted water

Publications (2)

Publication Number Publication Date
JP2002336604A true JP2002336604A (en) 2002-11-26
JP3920591B2 JP3920591B2 (en) 2007-05-30

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006263514A (en) * 2005-03-22 2006-10-05 Shimizu Corp Flocculation and dehydration method of muddy water
JP2010214248A (en) * 2009-03-13 2010-09-30 Toshiba Corp Solid-liquid separation system

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4875128B2 (en) * 2009-10-15 2012-02-15 株式会社東芝 Solid matter separation system

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100275004B1 (en) * 1998-09-25 2000-12-15 최춘식 High speed waste water disposal method

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006263514A (en) * 2005-03-22 2006-10-05 Shimizu Corp Flocculation and dehydration method of muddy water
JP2010214248A (en) * 2009-03-13 2010-09-30 Toshiba Corp Solid-liquid separation system

Also Published As

Publication number Publication date
TWI290911B (en) 2007-12-11
KR100697394B1 (en) 2007-03-20
CN1233574C (en) 2005-12-28
JP3920591B2 (en) 2007-05-30
CN1385374A (en) 2002-12-18
KR20020087854A (en) 2002-11-23

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