JPH07121387B2 - Organic wastewater treatment method - Google Patents
Organic wastewater treatment methodInfo
- Publication number
- JPH07121387B2 JPH07121387B2 JP28911787A JP28911787A JPH07121387B2 JP H07121387 B2 JPH07121387 B2 JP H07121387B2 JP 28911787 A JP28911787 A JP 28911787A JP 28911787 A JP28911787 A JP 28911787A JP H07121387 B2 JPH07121387 B2 JP H07121387B2
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- Prior art keywords
- organic wastewater
- air
- feeding
- wastewater
- flocculant
- Prior art date
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Description
【発明の詳細な説明】 〔産業上の利用分野〕 本発明は有機排水からBOD、COD、N−H(ノルマルヘキ
サン可溶性物質即ち油脂性物質)及び浮遊固形物質(S
S:suspended solid)(下文においてフロックと称する
こともある)を除去する有機排水の処理法に関する。DETAILED DESCRIPTION OF THE INVENTION [Industrial field of application] The present invention is applicable to BOD, COD, NH (normal hexane soluble substance or oily substance) and suspended solid substances (S
S: suspended solid) (sometimes referred to as flocs in the text below)
排水の浄化のために従来行われている方法としては化学
的処理法と生物学的処理法(活性汚泥法)並びに該二者
を併用したものが殆どである。高濃度のBOD、COD、N−
H、フロック(浮遊固形物質)等を含む原排水の処理に
当っては先ず薬注処理により多量の夾雑物を除いた後に
生物学的処理を行うのが通常である。この化学的処理に
よる分離方法には浮上又は沈殿の二法があり、前者は主
に有機物、後者は主に無機物の場合に用いられている。
しかも有機排水の分離の多くは薬注によりフロックを生
成させ凝集せしめた後に加圧水を注入するか又は空気を
積極的に注入して浮上分離させるのが通例である。Most conventional methods for purifying wastewater are chemical treatment methods and biological treatment methods (activated sludge method), and a combination of the two. High concentration of BOD, COD, N-
When treating raw wastewater containing H, flocs (suspended solid substances), etc., it is usual to first remove a large amount of contaminants by a chemical injection treatment and then perform a biological treatment. There are two methods of separation by this chemical treatment: floating or precipitation. The former is mainly used for organic substances and the latter is mainly used for inorganic substances.
Moreover, in most cases of separation of organic wastewater, it is customary to generate flocs by chemical injection to cause them to aggregate and then to inject pressurized water or positively inject air to effect floating separation.
上記の従来法における欠点として次の諸事項が挙げられ
る: (1)フロックの浮上速度が遅く、浮上分離までに通常
の場合に4〜5分間を要するので処理能力が低い; (2)多量の加圧水(原水に対し30〜40%)を使用する
から生物学的処理装置の容積の増大を招くと共に加圧水
製造装置を備える必要がある; 例えば原水100トンの処理のために30%の加圧水を使用
すると合計130トンという大量を扱うこととなるし、加
圧水で原水を押し上げるとフロックは95%以上の水分を
含有するものとなって処理を妨げ易くなる; (3)空気の積極的注入による方法では生成フロック及
び(又は)夾雑物の大きさにより浮上能力が左右され一
部大きいフロックは沈殿する場合があり、分離能力に問
題がある。即ち大きいフロックを浮上させるためには注
入時の空気量を多くするか又は空気通入圧力を増加する
必要があり、従って撹拌の状態を招くからフロックが浮
上し難く分離し難くなる; (4)浮上分離したフロックの水分含有量は一般に多く
(95%以上)従って後処理に不便である。The disadvantages of the above conventional method include the following items: (1) The flotation speed is slow, and it usually takes 4 to 5 minutes to float and separate, so that the throughput is low; The use of pressurized water (30-40% of the raw water) leads to an increase in the volume of the biological treatment equipment and it is necessary to have a pressurized water production device; for example, 30% of the pressurized water is used to treat 100 tons of raw water. Then, a large amount of 130 tons will be handled, and if the raw water is pushed up with pressurized water, flocs will contain 95% or more of water, making it easier to interfere with the treatment; (3) With the method by positively injecting air The flotation ability is influenced by the size of the produced flocs and / or impurities, and some large flocs may settle, resulting in a problem of separation ability. That is, in order to float a large floc, it is necessary to increase the amount of air at the time of injection or to increase the air-introducing pressure. Therefore, the state of agitation is caused, so that the floc is hard to float and difficult to separate; (4) The flocs separated by flotation generally have a high water content (95% or more) and are thus inconvenient for post-treatment.
以上のように浮上処理を行う必要のある有機排水就中食
品工場排水について本発明者は先に高速撹拌方式による
水産物工場排水の処理方法に関して特許(特許第101964
3号、特公昭55-6435号公報)を取得したがこの方法の欠
点は大量処理する場合の装置に問題が残ることにある。Regarding the organic wastewater that needs to be subjected to the floating treatment as described above, especially for the food factory wastewater, the present inventor has previously issued a patent regarding the method for treating the marine product factory wastewater by the high-speed stirring method (Patent No. 101964
No. 3, Japanese Examined Patent Publication No. 55-6435), but the drawback of this method is that the problem remains in the equipment for large-scale processing.
本発明者は従前技術及び上記特許の方法の改良について
種々実験を重ねた結果ジェット方式により満足すべき成
果を得ることができた。The inventor has obtained various satisfactory results by the jet method as a result of various experiments conducted on the improvements of the prior art and the method of the above patent.
本発明の特徴とする点は下記の通りである: (1)予めpH値が調整され、及び(又は)凝集剤が添加
されている有機排水からBOD、COD、N−H及び浮遊固形
物質を除去する有機排水の処理方法において、被処理排
水を約2m以上の高さからジェットエジクターの中へ加圧
下に噴出させ、該噴出によって減圧状態を形成させ、該
状態下に空気吸入及び高分子凝集剤溶液の吸入を伴いな
がら被処理排水を浮遊固形物質浮上分離手段の中に落下
させるか又は該手段の水面に落下させ、かようにして短
時間内に浮遊固形物質を分離させる上記の方法。The features of the present invention are as follows: (1) BOD, COD, NH, and suspended solid substances are removed from an organic wastewater having a pH value adjusted in advance and / or a coagulant added thereto. In the method for treating organic wastewater to be removed, the wastewater to be treated is jetted under pressure into the jet ejector from a height of about 2 m or more, and a reduced pressure state is formed by the jetting, and air suction and polymer The above-mentioned method in which the wastewater to be treated is dropped into the floating solid substance floating separation means while inhaling the flocculant solution or is dropped onto the water surface of the means, and thus the floating solid substances are separated within a short time. .
(2)有機排水送給手段、pH調整剤及び(又は)凝集剤
送給手段、有機排水とpH調整剤及び(又は)凝集剤とを
混合する混合手段、該手段により得られた混合液に空気
と高分子凝集剤溶液とを送給添加する送給手段及び該送
給添加後に浮遊固形物質を分離する分離手段を具備する
有機排水の処理装置において、混合手段と分離手段との
中間に混合液を噴出させ落下させるためのジェットエジ
ェクターを設けると共に該エジェクターの減圧状態形成
箇所へ空気と高分子凝集剤とを吸入させることによって
送給する送給口を設けた上記の装置。(2) Organic wastewater feeding means, pH adjusting agent and / or coagulant feeding means, mixing means for mixing the organic wastewater with the pH adjusting agent and / or coagulant, and the mixed liquid obtained by the means In an organic wastewater treatment apparatus comprising a feeding means for feeding and adding air and a polymer flocculant solution and a separating means for separating floating solid substances after the feeding and adding, mixing is performed between the mixing means and the separating means. The apparatus described above, which is provided with a jet ejector for ejecting and dropping the liquid, and with a supply port for supplying air and a polymer coagulant by sucking air and a polymer coagulant to a reduced pressure state forming portion of the ejector.
以下に図面を参照して本発明を詳細に説明する。Hereinafter, the present invention will be described in detail with reference to the drawings.
有機排水特に食品工場からの排水をポンプ(P)の使用
下に流量調整槽(L)を介して一定の流量を保つ速度で
混合槽(1)又は(2)へ送る。操業をバッチ式或いは
連続式又は両者併用方式で行い得る。混合槽内の被処理
排水へポンプ(P)使用下に、pH調整剤例えば苛性ソー
ダ水溶液又は排水処理に常用される化学物質(消石灰、
塩酸など)を調整剤貯槽(5)からポンプ(P)を介し
て加え、pHメーター使用下に混和してフロックを生成さ
せる。Organic wastewater, especially wastewater from a food factory, is sent to a mixing tank (1) or (2) at a rate that maintains a constant flow rate through a flow rate adjusting tank (L) while using a pump (P). The operation can be performed in a batch system, a continuous system, or a combination of both systems. Using a pump (P) to the wastewater to be treated in the mixing tank, a pH adjuster such as an aqueous solution of caustic soda or a chemical substance (slaked lime,
Hydrochloric acid or the like) is added from a regulator storage tank (5) through a pump (P), and mixed by using a pH meter to generate flocs.
pH調整と同時に又は別個に或いはpH調整せずに硫酸バン
ド又はPAC(ポリ塩化アルミニウムの略称;本発明では
多木化学株式会社製のものを用いた)等の凝集剤を凝集
剤貯槽(5)からポンプ(P)を介し混合槽へ添加混合
してフロックを生成させてもよい。かように予備処理し
た混合液(被処理水)をジェットエジェクターへ送入す
る場合には約2.0〜7.0気圧の圧力を必要とするので通常
は多段式タービンポンプ(図示せず)を使用する。A flocculant such as a sulfuric acid band or PAC (abbreviation of polyaluminum chloride; used by Taki Kagaku Co., Ltd. in the present invention) was added to the flocculant storage tank (5) simultaneously with or separately from pH adjustment or without pH adjustment. From the above, a floc may be generated by adding and mixing it to the mixing tank via the pump (P). When the mixed solution (water to be treated) thus pretreated is fed to the jet ejector, a pressure of about 2.0 to 7.0 atm is required, so a multistage turbine pump (not shown) is usually used.
本発明においてもジェットエジェクターにセットした該
タービンポンプの使用下に高さ約2m以上のところから約
2.0気圧以上の加圧下にジェットエジェクターの入口
(8)からノズル(9)を通って混合液を落下させる。
この場合に従前技術におけるような加圧水の添加を行う
ことなく混合液のみを落下させる。その際落下水は機内
に減圧状態を形成すると共に空気の吸入により気泡を保
持して落下水からのフロックの浮上分離を容易にする。Also in the present invention, when the turbine pump set in the jet ejector is used, a height of about 2 m or more
The mixture is dropped from the jet ejector inlet (8) through the nozzle (9) under a pressure of 2.0 atm or more.
In this case, only the mixed solution is dropped without adding pressurized water as in the prior art. At that time, the falling water forms a depressurized state in the machine, and the air is sucked to hold air bubbles to facilitate the floating separation of the flocs from the falling water.
吸入による空気供給のための該供給口(6−A)に調整
バルブを設けて機内の減圧度を一定に保たせる。同時に
高分子凝集剤溶液貯槽(3)から高分子凝集剤溶液をジ
ェットエジェクターの中へ機内の減圧の利用によって供
給口(6−B)を経て送り込み混合液と混和しながら落
下させる。供給口(6−B)に調整バルブと流量計とを
設けて高分子凝集剤溶液の添加量を調整する。高分子凝
集剤としては市販の各種製品を使用し得るが本発明にお
いて好適に用いられるものは例えば日本純薬(株)製商
標名アロンビス、栗田工業(株)製商標名クリフロッ
ク、多木化学(株)製商標名タキフロック、三井サイア
ナミッド(有)製商標名アコフロック等である。高分子
凝集剤の添加量は常法に従い被処理排水に対し5〜60PP
M、平均30PPM前後である。An adjusting valve is provided at the supply port (6-A) for supplying air by suction so that the degree of pressure reduction inside the machine can be kept constant. At the same time, the polymer coagulant solution is sent from the polymer coagulant solution storage tank (3) into the jet ejector through the supply port (6-B) by utilizing the reduced pressure in the machine and dropped while being mixed with the mixed solution. An adjusting valve and a flow meter are provided at the supply port (6-B) to adjust the addition amount of the polymer coagulant solution. As the polymer flocculant, various commercially available products can be used, but those which are preferably used in the present invention are, for example, Nippon Pure Chemical Co., Ltd. trade name Aronbis, Kurita Kogyo Co., Ltd. trade name Cliflock, Taki Kagaku. The trademark name is Takiflock manufactured by Mitsui Co., Ltd., the trademark name Akofrock manufactured by Mitsui Cyanamid Co., Ltd., and the like. The amount of polymer flocculant added is 5 to 60 PP for the wastewater to be treated according to the conventional method.
M, around 30PPM on average.
落下水はジェットエジェクターの吐出口(12)から浮上
分離槽(7)の中に落下すると短時間10秒前後でフロッ
クを浮上分離する。分離液はこれを常法に従って分離し
排出させる。When the falling water falls from the jet ejector discharge port (12) into the flotation separation tank (7), the flocs are floated and separated within about 10 seconds in a short time. The separated liquid is separated and discharged according to a conventional method.
本発明によるフロック浮上分離の短時間10秒前後におけ
る達成に際し考えられる分離条件は下記の通りである: (1)ジェットエジェクターへ送給する被処理排水に対
する圧力を一定にすること; (2)ジェットエジェクターの吸入口即ち送給口からの
空気及び高分子凝集剤溶液の送給量をフロックの浮上分
離が10秒前後となるように調整すること; (3)混合液調整に凝集剤を使用する場合にもフロック
の浮上分離が所期の短時間に達成される量で該凝集剤を
使用すること。The separation conditions that can be considered when achieving floc float separation according to the present invention in a short time of about 10 seconds are as follows: (1) Keeping the pressure of the treated wastewater fed to the jet ejector constant (2) Jet Adjust the amount of air and polymer flocculant solution fed from the ejector suction port, that is, the feed port, so that the flocculation separation of flocs is about 10 seconds; (3) Use a flocculant to prepare the mixture If necessary, use the flocculant in an amount such that flot flotation is achieved in the desired short time.
上記の諸条件の組合せの作用が本法を成功させると考え
られる。It is believed that the action of the combination of the above conditions will make the method successful.
実施例1 BOD 5000PPM、COD 3200PPM、浮遊固形物質1800PPM、N
−H 500PPMを有する鯖の洗浄排水に対しPACを加えてpH
5.0付近に調整した後に毎時30m3/時の量で、三段ター
ビンポンプにより地上3mの高さに設置したマルチジェッ
トエジェクターの中へ該調整排水を直接落下せしめると
共にその際生じる減圧度を利用して高分子凝集剤(商標
名アコフロックC447)の30PPMを添加した所浮上分離は
瞬時(約10秒以下)にして行われ、BOD約80%が除去さ
れ、残留浮遊固形物質は10PPM、N−H残存量は1PPM以
下であった。Example 1 BOD 5000PPM, COD 3200PPM, suspended solids 1800PPM, N
-H Addition of PAC to the cleaning wastewater of mackerel with 500 PPM
After adjusting it to around 5.0, the adjusted drainage is dropped directly into the multi-jet ejector installed at a height of 3 m above the ground by a three-stage turbine pump at an amount of 30 m 3 / hour and the degree of pressure reduction produced at that time is used. After adding 30PPM of polymer flocculant (Trade name: Akofloc C447), floatation separation is performed instantly (about 10 seconds or less), BOD of about 80% is removed, and residual suspended solid matter is 10PPM, NH The residual amount was 1 PPM or less.
実施例2 BOD 1800PPM、COD 860PPM、N−H 60PPM、浮遊固形物質
350PPMを有する麺類製造工場からの排水を消石灰でpH8.
5としてからPAC300PPMを加えた後に充分に混和して前記
と同様にジェットエジェクターを用いて浮上分離せしめ
た結果、フロックの浮上分離、分離時間は実施例1にお
けると全く同様であった。なお製麺工場排水の場合には
消石灰の使用で被処理水をアルカリ側にpH調整した後に
通常処理を行う方がフロック形成が良好であり、従って
浮上分離も容易となる。Example 2 BOD 1800PPM, COD 860PPM, NH 60PPM, suspended solids
Wastewater from a noodle manufacturing plant with 350 PPM is adjusted to pH 8 with slaked lime.
After adding PAC300PPM after 5, the mixture was thoroughly mixed and floated and separated by using a jet ejector in the same manner as described above. As a result, flok floating and separation time were exactly the same as in Example 1. In the case of wastewater from a noodle factory, the floc formation is better and the flotation is easier when the normal treatment is performed after adjusting the pH of the water to be treated to the alkaline side by using slaked lime.
本発明の効果は従来法におけるような空気の積極的注入
によることなく、又は加圧水を使用することなく瞬時
(10秒前後)にしてフロックを浮上分離させ、分離した
フロックの含水量も従来法におけるものよりかなり低く
85〜90%程度であり、且つ大量処理設備は簡易であり、
費用も極めて低廉である点にある。The effect of the present invention is that the flocs are floated and separated instantly (around 10 seconds) without actively injecting air as in the conventional method or without using pressurized water, and the water content of the separated flocs is also in the conventional method. Much lower than
85-90%, and the mass processing equipment is simple,
The cost is also extremely low.
添付図面の第1図は本発明の装置及び各手段の配置の概
要を示す。第2図は本発明で使用するジェットエジェク
ターの一例を示す。 1及び2……混合槽、3……高分子凝集剤液貯槽、4…
…アルカリ液貯槽、5……PAC液貯槽、6……ジェット
エジェクター、6A……空気送給口、6B……高分子凝集剤
液送給口、7……分離槽、8……加圧された混合液入
口、9……ノズル、10……スロート、11……ディフュー
ザー、12……吐出口、L……流量調整槽、P……ポン
プ、PH……pH値測定器、M……撹拌機、F……浮上フロ
ック、T……処理水。FIG. 1 of the accompanying drawings outlines the arrangement of the device and each means of the present invention. FIG. 2 shows an example of the jet ejector used in the present invention. 1 and 2 ... Mixing tank, 3 ... Polymer flocculant liquid storage tank, 4 ...
… Alkaline liquid storage tank, 5 …… PAC liquid storage tank, 6 …… Jet ejector, 6A …… Air supply port, 6B …… Polymer flocculant liquid supply port, 7 …… Separation tank, 8 …… Pressurized Mixed liquid inlet, 9 ... Nozzle, 10 ... Throat, 11 ... Diffuser, 12 ... Discharge port, L ... Flow rate adjusting tank, P ... Pump, PH ... pH value measuring device, M ... Agitation Machine, F ... levitating floc, T ... treated water.
Claims (2)
が添加されている有機排水からBOD、COD、N−H及び浮
遊固形物質を除去する有機排水の処理方法において、被
処理排水を約2m以上の高さからジェットエジェクターの
中へ加圧下に噴出させ、該噴出によって減圧状態を形成
させ、該状態下に空気吸入及び高分子凝集剤溶液の吸入
を伴いながら被処理排水を浮遊固形物質浮上分離手段の
中に落下させるか又は該手段の水面に落下させ、かよう
にして短時間内に浮遊固形物質を浮上分離させることを
特徴とする上記の方法。1. A method for treating organic wastewater, wherein BOD, COD, NH, and suspended solid substances are removed from the organic wastewater having a pH value adjusted in advance and / or a coagulant added thereto. Is ejected from a height of about 2 m or more into the jet ejector under pressure, a depressurized state is formed by the ejection, and the treated wastewater is suspended while inhaling air and the polymer coagulant solution under the state. The method as described above, characterized in that it is dropped into the solid material floating separation means or dropped onto the water surface of the means, and thus the floating solid material is floated and separated within a short time.
凝集剤送給手段、有機排水とpH調整剤及び(又は)凝集
剤とを混合する混合手段、該手段により得られた混合液
に空気と高分子凝集剤溶液とを送給添加する送給手段及
び送給添加後に浮遊固形物質を分離する分離手段を具備
する有機排水の処理装置において、混合手段と分離手段
との中間に混合液を噴出させ落下させるジェットエジェ
クターを設けると共に該エジェクターの減圧状態形成箇
所へ空気と高分子凝集剤とを吸入させることによって送
給する送給口を設けたことを特徴とする上記の装置。2. Organic wastewater feeding means, pH adjusting agent and / or
Flocculant feeding means, mixing means for mixing organic wastewater with pH adjusting agent and / or flocculant, and feeding means for feeding and adding air and polymer flocculant solution to the mixed liquid obtained by the means In a treatment apparatus for organic wastewater having a separating means for separating suspended solid substances after feeding and adding, a jet ejector for ejecting and dropping the mixed liquid is provided between the mixing means and the separating means, and a reduced pressure state of the ejector is formed. The above-mentioned device, which is provided with a supply port for supplying air and polymer coagulant by inhaling the air and the polymer coagulant.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP28911787A JPH07121387B2 (en) | 1987-11-16 | 1987-11-16 | Organic wastewater treatment method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP28911787A JPH07121387B2 (en) | 1987-11-16 | 1987-11-16 | Organic wastewater treatment method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH01130776A JPH01130776A (en) | 1989-05-23 |
| JPH07121387B2 true JPH07121387B2 (en) | 1995-12-25 |
Family
ID=17739000
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP28911787A Expired - Lifetime JPH07121387B2 (en) | 1987-11-16 | 1987-11-16 | Organic wastewater treatment method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH07121387B2 (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2529174B2 (en) * | 1992-09-17 | 1996-08-28 | 和泉電気株式会社 | Method and device for floating separation of suspended particles in liquid |
| GB0809603D0 (en) * | 2008-05-28 | 2008-07-02 | Vws Westgarth Ltd | Fluid treatment apparatus |
| WO2018199703A1 (en) * | 2017-04-28 | 2018-11-01 | 엘지전자 주식회사 | Method for reporting channel state information in wireless communication system and apparatus therefor |
-
1987
- 1987-11-16 JP JP28911787A patent/JPH07121387B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPH01130776A (en) | 1989-05-23 |
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