JP2000254638A - Treatment of metal-containing waste water and its device - Google Patents
Treatment of metal-containing waste water and its deviceInfo
- Publication number
- JP2000254638A JP2000254638A JP11066960A JP6696099A JP2000254638A JP 2000254638 A JP2000254638 A JP 2000254638A JP 11066960 A JP11066960 A JP 11066960A JP 6696099 A JP6696099 A JP 6696099A JP 2000254638 A JP2000254638 A JP 2000254638A
- Authority
- JP
- Japan
- Prior art keywords
- metal
- containing wastewater
- waste water
- wastewater
- flocks
- 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
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- Physical Water Treatments (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は金属含有排水の処理
方法及び装置に係り、特に排水中の金属イオンを水酸化
物として凝集させ浮上分離する方法及び装置に関するも
のである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for treating metal-containing wastewater, and more particularly to a method and an apparatus for aggregating metal ions in the wastewater as hydroxide to separate them by flotation.
【0002】[0002]
【従来の技術】金属含有排水特に重金属含有排水の処理
方法としては、アルカリを添加して金属水酸化物フロッ
クを生成させ、これを沈降分離して除去する方法が広く
採用されている。また、この金属水酸化物フロックを凝
集濾過する方法も採用されている。さらに、イオン交換
法により金属を除去する方法も行われている。2. Description of the Related Art As a method for treating metal-containing wastewater, especially heavy metal-containing wastewater, a method of adding an alkali to form a metal hydroxide floc and sedimenting and separating the floc has been widely adopted. A method of coagulating and filtering this metal hydroxide floc is also employed. Further, a method of removing a metal by an ion exchange method is also performed.
【0003】[0003]
【発明が解決しようとする課題】金属含有排水にアルカ
リを添加し金属水酸化物フロックを凝集沈降分離する方
法の場合、凝集槽と沈殿槽とを必要とし、装置の設置ス
ペースが大きい。The method of coagulating sedimentation of metal hydroxide flocs by adding alkali to metal-containing wastewater requires a coagulation tank and a sedimentation tank, and requires a large installation space for the apparatus.
【0004】凝集濾過法にあっては、排水中の金属濃度
が高いと逆洗頻度が増すなど運転効率が低下する。イオ
ン交換法は、低濃度の金属含有排水の処理には適する
が、高濃度の金属含有排水の処理には適さない。[0004] In the coagulation filtration method, when the metal concentration in the wastewater is high, the operation efficiency decreases, such as the frequency of backwashing increases. The ion exchange method is suitable for treating low-concentration metal-containing wastewater, but is not suitable for treating high-concentration metal-containing wastewater.
【0005】本発明は高濃度の金属含有排水であっても
効率良く処理することができる金属含有排水の処理方法
及び装置を提供することを目的とする。An object of the present invention is to provide a method and an apparatus for treating metal-containing wastewater which can efficiently treat even high-concentration metal-containing wastewater.
【0006】[0006]
【課題を解決するための手段】本発明の金属含有排水の
処理方法は、金属含有排水にアルカリと過酸化水素とを
添加し、生成する金属水酸化物フロックを発生する気泡
によって浮上分離することを特徴とするものである。According to the present invention, there is provided a method for treating a metal-containing wastewater, comprising adding an alkali and hydrogen peroxide to the metal-containing wastewater and separating the metal-containing wastewater by air bubbles which generate metal hydroxide flocs. It is characterized by the following.
【0007】また、本発明の金属含有排水の処理装置
は、金属含有排水にアルカリと過酸化水素とを添加する
手段と、金属水酸化物フロックを浮上分離する分離手段
とを有するものである。Further, the apparatus for treating metal-containing waste water of the present invention has means for adding alkali and hydrogen peroxide to metal-containing waste water, and separation means for floating and separating metal hydroxide flocs.
【0008】かかる本発明の方法及び装置にあっては、
排水中の金属イオンは、添加されたアルカリによって金
属水酸化物フロックとなる。また、添加された過酸化水
素は、アルカリ性の液中では分解して酸素を発生させ、
この酸素気泡が金属水酸化物フロックに付着して該フロ
ックを浮上させる。このようにして、本発明によると、
排水中の金属イオンを金属水酸化物フロックとして急速
に浮上分離することができる。In the method and apparatus according to the present invention,
The metal ions in the wastewater become metal hydroxide flocs due to the added alkali. Also, the added hydrogen peroxide decomposes in an alkaline liquid to generate oxygen,
The oxygen bubbles adhere to the metal hydroxide flocs and cause the flocs to float. Thus, according to the present invention,
Metal ions in wastewater can be rapidly floated and separated as metal hydroxide flocs.
【0009】本発明では、浮上分離手段としては、傾斜
板で区画された複数の区画室と、各区画室の上部に被分
離処理液を導入する手段と、各区画室の下部から処理水
を流出させる手段とを有するものが好ましい。In the present invention, the floating separation means includes a plurality of compartments divided by an inclined plate, a means for introducing a liquid to be treated into the upper part of each compartment, and a process water flowing out from the lower part of each compartment. What has a means is preferable.
【0010】[0010]
【発明の実施の形態】本発明において、処理対象となる
金属含有排水は、金属イオン特に重金属イオンを含む排
水である。重金属イオンとしては、例えばFe,Cu,
Mn,Cr,Co,Ni,Zn,CdなどアルカリpH
域にて水不溶性の水酸化物を生じさせるものが挙げられ
る。この重金属イオンの濃度は50〜5000mg/L
程度である場合に本発明方法及び装置によって処理する
のに適当であり、必要に応じこの濃度範囲となるように
濃縮したり逆に稀釈する。BEST MODE FOR CARRYING OUT THE INVENTION In the present invention, metal-containing wastewater to be treated is wastewater containing metal ions, particularly heavy metal ions. Examples of heavy metal ions include Fe, Cu,
Alkaline pH such as Mn, Cr, Co, Ni, Zn, Cd
One that produces a water-insoluble hydroxide in the region. The concentration of this heavy metal ion is 50-5000 mg / L
If so, it is suitable for processing by the method and apparatus of the present invention, and if necessary, it is concentrated or conversely diluted to this concentration range.
【0011】この金属含有排水の具体例としては、メッ
キ排水、排煙脱硫排水、写真現像液排水などが例示され
る。Specific examples of the metal-containing wastewater include plating wastewater, flue gas desulfurization wastewater, and photographic developer wastewater.
【0012】重金属含有排水に添加するアルカリは水溶
液として添加されるのが好ましい。アルカリとしては、
NaOH,KOH,Ca(OH)2,CaO,Na2CO
3等を用いることができるが、コスト及び溶解性の点か
らNaOHが好適である。NaOHの場合、10〜60
wt%程度の濃度の水溶液として金属含有排水に添加す
るのが好ましい。The alkali added to the heavy metal-containing waste water is preferably added as an aqueous solution. As the alkali,
NaOH, KOH, Ca (OH) 2, CaO, Na 2 CO
Although 3 and the like can be used, NaOH is preferred from the viewpoint of cost and solubility. In the case of NaOH, 10 to 60
It is preferable to add to the metal-containing wastewater as an aqueous solution having a concentration of about wt%.
【0013】アルカリは、添加後の金属含有排水のpH
が6〜12とくに9〜11程度となるように添加される
のが好ましい。The alkali is the pH of the metal-containing waste water after the addition.
Is preferably added so as to be about 6 to 12, particularly about 9 to 11.
【0014】過酸化水素は、10〜50wt%程度の水
溶液として添加されるのが好ましい。過酸化水素は排水
に対し、添加後の該排水中の過酸化水素濃度が0.01
〜10mg/Lとくに0.05〜3mg/L程度となる
ように添加されるのが好ましい。The hydrogen peroxide is preferably added as an aqueous solution of about 10 to 50% by weight. Hydrogen peroxide was added to the wastewater at a concentration of 0.01% in the wastewater after the addition.
It is preferably added to be about 10 to 10 mg / L, particularly about 0.05 to 3 mg / L.
【0015】アルカリと過酸化水素とはいずれを先に金
属含有排水に添加しても良く、同時に添加しても良い。
アルカリ及び/又は過酸化水素を金属含有排水に添加し
た後、該排水を適度な攪拌強さで攪拌しても良い。アル
カリ及び/又は過酸化水素は、浮上分離槽に入る前の排
水に添加されても良く、浮上分離槽内において排水に添
加されても良い。Any of the alkali and the hydrogen peroxide may be added to the metal-containing wastewater first, or may be added simultaneously.
After adding the alkali and / or hydrogen peroxide to the metal-containing wastewater, the wastewater may be stirred with an appropriate stirring strength. The alkali and / or hydrogen peroxide may be added to the wastewater before entering the flotation tank, or may be added to the wastewater in the flotation tank.
【0016】なお、過酸化水素から発生する酸素気泡だ
けではフロックを十分に浮上させることができない場合
には、銅、鉄、マンガン、クロムなどの水溶性の塩(例
えば塩化物、硫酸塩、硝酸塩など)を排水に少量添加し
ても良い。If the flocs cannot be sufficiently floated by oxygen bubbles generated from hydrogen peroxide alone, water-soluble salts such as copper, iron, manganese, and chromium (eg, chlorides, sulfates, nitrates) ) May be added to the wastewater in small amounts.
【0017】この浮上分離槽は、内部が傾斜板によって
複数の区画室に区画され、分離効率を高めたものが好ま
しい。傾斜板の傾斜角度は10〜60°程度が好適であ
る。また、傾斜板相互の間隔は10〜500mm程度が
好適である。The flotation tank preferably has an interior partitioned into a plurality of compartments by an inclined plate to enhance the separation efficiency. The inclination angle of the inclined plate is preferably about 10 to 60 °. The interval between the inclined plates is preferably about 10 to 500 mm.
【0018】図1は本発明の実施の形態に係る金属含有
排水の浮上分離処理装置の概略的な縦断面図である。FIG. 1 is a schematic vertical sectional view of an apparatus for separating and floating a metal-containing wastewater according to an embodiment of the present invention.
【0019】この処理装置は、金属含有排水の導入用の
配管10と、浮上分離槽20と、浮上した汚泥(フロッ
ク)の取出部30と、処理水の取出用の配管40とを備
えている。This treatment apparatus is provided with a pipe 10 for introducing metal-containing wastewater, a flotation tank 20, a take-out section 30 for taking up sludge (flock), and a pipe 40 for taking out treated water. .
【0020】浮上分離槽20内は複数枚の傾斜板24に
よって複数の区画室26に区画されている。各傾斜板2
4は、上端側が一方の槽壁21から離隔し、下端側は他
方の槽壁22に連結されている。金属含有排水導入用配
管10は区画室26と同数本の分岐配管12に分岐し、
各区画室26内に差し込まれている。この分岐配管12
には、過酸化水素水溶液の添加用の配管14と、アルカ
リ(この実施の形態では水酸化ナトリウム)水溶液の添
加用の配管16とが接続されている。The flotation tank 20 is divided into a plurality of compartments 26 by a plurality of inclined plates 24. Each inclined plate 2
4 has an upper end separated from one tank wall 21 and a lower end connected to the other tank wall 22. The metal-containing drainage introduction pipe 10 branches into the same number of branch pipes 12 as the compartment 26,
It is inserted into each compartment 26. This branch pipe 12
Is connected to a pipe 14 for adding an aqueous solution of hydrogen peroxide and a pipe 16 for adding an aqueous solution of alkali (sodium hydroxide in this embodiment).
【0021】汚泥取出部30は、浮上分離槽20の上端
部外周の少なくとも一部を囲むように設けられており、
槽20の上端をオーバーフローした汚泥が該取出部30
内に流入し、汚泥排出管32から取り出されるようにな
っている。なお、槽20の上部に汚泥の掻き取り装置を
設けても良い。The sludge take-out section 30 is provided so as to surround at least a part of the outer periphery of the upper end portion of the flotation tank 20.
The sludge that overflows the upper end of the tank 20 is discharged from the discharge unit 30.
And is taken out from the sludge discharge pipe 32. Note that a sludge scraping device may be provided above the tank 20.
【0022】重金属含有排水は、分岐配管12において
NaOH及びH2O2が添加された後、浮上分離槽20内
に流入する。このNaOHの添加により重金属イオンが
水酸化物フロックになると共に、H2O2が分解してO2
ガスを生じさせ、このO2ガスが水酸化物フロックに付
着してフロックを浮上させる。このフロックは槽20か
ら取出部30を経て取り出される。フロックが分離され
た液は処理水取出配管40から取り出される。The heavy metal-containing wastewater flows into the flotation tank 20 after NaOH and H 2 O 2 are added in the branch pipe 12. The addition of this NaOH causes heavy metal ions to become hydroxide flocs and decomposes H 2 O 2 to O 2
A gas is generated, and this O 2 gas adheres to the hydroxide flocs to lift the flocs. This floc is taken out of the tank 20 through the take-out part 30. The liquid from which the flocs have been separated is taken out from the treated water take-out pipe 40.
【0023】[0023]
【実施例】以下、図1の装置を用いて塩化第2銅の50
0ppm水溶液を処理した実験例について説明する。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS In the following, 50 cupric chloride was prepared using the apparatus shown in FIG.
An experimental example in which a 0 ppm aqueous solution is treated will be described.
【0024】この水溶液に対しNaOHの10N水溶液
を添加後のpHが11となるように添加すると共に、H
2O2の35wt%水溶液を添加後の水中のH2O2濃度が
表1の各濃度となるように添加した。To this aqueous solution, a 10N aqueous solution of NaOH was added so that the pH after the addition became 11, and H
Concentration of H 2 O 2 in water after addition of 35 wt% aqueous solution of 2 O 2 was added so that the respective concentrations shown in Table 1.
【0025】浮上分離槽20へはこの液を1m3/Hr
の流入速度で流入させた。傾斜板24の傾斜角度は30
°であり、傾斜板24の上下の間隔は200mmであ
り、傾斜板24の傾斜方向長さは500mmであり、区
画室26の数は3室である。This liquid is supplied to the flotation tank 20 at 1 m 3 / Hr
At an inflow speed of. The inclination angle of the inclined plate 24 is 30
°, the vertical interval of the inclined plate 24 is 200 mm, the length of the inclined plate 24 in the inclined direction is 500 mm, and the number of the compartments 26 is three.
【0026】処理水取出用配管40から流出する単位時
間当りのスラッジ量の測定結果を表1に併せて示す。Table 1 also shows the measurement results of the amount of sludge flowing out of the treated water discharge pipe 40 per unit time.
【0027】[0027]
【表1】 [Table 1]
【0028】表1の通り、この実験例では過酸化水素を
13mg/L以上添加することにより重金属スラッジ
(フロック)の流出が完全に防止されることが分る。As shown in Table 1, in this experimental example, it is found that the outflow of heavy metal sludge (flock) is completely prevented by adding hydrogen peroxide at 13 mg / L or more.
【0029】なお、塩化第2銅水溶液の濃度を1000
mg/L又は1500mg/Lとしたこと以外は同様の
実験を行ったところ、過酸化水素35%水溶液を前者の
場合は26mg/L以上、後者の場合は39mg/L以
上添加することによりフロック流出が完全に防止される
ことが認められた。The concentration of the cupric chloride aqueous solution is set to 1000
The same experiment was carried out except that the concentration was changed to 25 mg / L or 1500 mg / L. Floc efflux was caused by adding a 35% aqueous solution of hydrogen peroxide to the former by 26 mg / L or more, and the latter to 39 mg / L or more. Was completely prevented.
【0030】塩化第2銅の代わりに塩化第2鉄、塩化第
2マンガン、塩化第2クロムを用いた場合もほぼ同程度
の水酸化ナトリウム及び過酸化水素の添加によりフロッ
ク流出が完全に防止されることが認められた。When ferric chloride, manganese chloride and chromium chloride are used in place of cupric chloride, the floc outflow is completely prevented by adding sodium hydroxide and hydrogen peroxide at substantially the same level. Was recognized.
【0031】[0031]
【発明の効果】以上の通り、本発明によると排水中の重
金属イオンを効率良く除去できる。また本発明による
と、設置スペースの小さい金属含有排水処理装置が提供
される。As described above, according to the present invention, heavy metal ions in wastewater can be efficiently removed. Further, according to the present invention, there is provided a metal-containing wastewater treatment apparatus having a small installation space.
【図1】本発明の実施の形態に係る金属含有排水の浮上
分離処理装置の概略的な縦断面図である。FIG. 1 is a schematic vertical cross-sectional view of a floating separation treatment apparatus for metal-containing wastewater according to an embodiment of the present invention.
20 浮上分離槽 21,22 槽壁 24 傾斜板 26 区画室 30 汚泥取出部 Reference Signs List 20 flotation separation tank 21, 22 tank wall 24 inclined plate 26 compartment 30 sludge discharge section
Claims (3)
を添加し、生成する金属水酸化物フロックを発生する気
泡によって浮上分離することを特徴とする金属含有排水
の処理方法。1. A method for treating metal-containing wastewater, comprising adding an alkali and hydrogen peroxide to the metal-containing wastewater, and separating the metal-containing wastewater by air bubbles that generate metal hydroxide flocs.
を添加する手段と、金属水酸化物フロックを浮上分離す
る分離手段とを有する金属含有排水の処理装置。2. An apparatus for treating metal-containing wastewater, comprising: means for adding alkali and hydrogen peroxide to metal-containing wastewater; and separation means for floating and separating metal hydroxide flocs.
斜板で区画された複数の区画室と、各区画室の上部に被
分離処理液を導入する手段と、各区画室の下部から処理
水を流出させる手段とを有することを特徴とする金属含
有排水の処理装置。3. The method according to claim 2, wherein the separation unit includes a plurality of compartments partitioned by an inclined plate, a unit for introducing a liquid to be separated into the upper portion of each compartment, and a process water from a lower portion of each compartment. Means for draining metal-containing wastewater.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP11066960A JP2000254638A (en) | 1999-03-12 | 1999-03-12 | Treatment of metal-containing waste water and its device |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP11066960A JP2000254638A (en) | 1999-03-12 | 1999-03-12 | Treatment of metal-containing waste water and its device |
Publications (1)
Publication Number | Publication Date |
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JP2000254638A true JP2000254638A (en) | 2000-09-19 |
Family
ID=13331110
Family Applications (1)
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JP11066960A Pending JP2000254638A (en) | 1999-03-12 | 1999-03-12 | Treatment of metal-containing waste water and its device |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2002320979A (en) * | 2001-04-27 | 2002-11-05 | Sharp Corp | Method and system for treating metal-containing drainage |
WO2003042108A1 (en) * | 2001-11-14 | 2003-05-22 | Ebara Corporation | Method of floatation separation treatment of raw water |
-
1999
- 1999-03-12 JP JP11066960A patent/JP2000254638A/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2002320979A (en) * | 2001-04-27 | 2002-11-05 | Sharp Corp | Method and system for treating metal-containing drainage |
WO2003042108A1 (en) * | 2001-11-14 | 2003-05-22 | Ebara Corporation | Method of floatation separation treatment of raw water |
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