JPS6312678B2 - - Google Patents
Info
- Publication number
- JPS6312678B2 JPS6312678B2 JP4118783A JP4118783A JPS6312678B2 JP S6312678 B2 JPS6312678 B2 JP S6312678B2 JP 4118783 A JP4118783 A JP 4118783A JP 4118783 A JP4118783 A JP 4118783A JP S6312678 B2 JPS6312678 B2 JP S6312678B2
- Authority
- JP
- Japan
- Prior art keywords
- wastewater
- filler
- pollutants
- aluminum
- electrodes
- 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
Links
- 239000002351 wastewater Substances 0.000 claims description 34
- 239000000945 filler Substances 0.000 claims description 22
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 14
- 239000003344 environmental pollutant Substances 0.000 claims description 12
- 231100000719 pollutant Toxicity 0.000 claims description 12
- 229910052782 aluminium Inorganic materials 0.000 claims description 9
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical group [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 claims description 9
- 229910052742 iron Inorganic materials 0.000 claims description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 claims description 6
- 238000005868 electrolysis reaction Methods 0.000 claims description 5
- 238000004065 wastewater treatment Methods 0.000 claims description 5
- 239000011810 insulating material Substances 0.000 claims description 3
- 230000001112 coagulating effect Effects 0.000 claims 1
- 238000006243 chemical reaction Methods 0.000 description 12
- 239000000463 material Substances 0.000 description 10
- 238000000034 method Methods 0.000 description 5
- 239000000654 additive Substances 0.000 description 4
- 238000012423 maintenance Methods 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 2
- WNROFYMDJYEPJX-UHFFFAOYSA-K aluminium hydroxide Chemical compound [OH-].[OH-].[OH-].[Al+3] WNROFYMDJYEPJX-UHFFFAOYSA-K 0.000 description 2
- VSCWAEJMTAWNJL-UHFFFAOYSA-K aluminium trichloride Chemical compound Cl[Al](Cl)Cl VSCWAEJMTAWNJL-UHFFFAOYSA-K 0.000 description 2
- 239000000460 chlorine Substances 0.000 description 2
- 229910052801 chlorine Inorganic materials 0.000 description 2
- -1 chlorine ions Chemical class 0.000 description 2
- 238000005188 flotation Methods 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 150000004679 hydroxides Chemical class 0.000 description 2
- 235000014413 iron hydroxide Nutrition 0.000 description 2
- NCNCGGDMXMBVIA-UHFFFAOYSA-L iron(ii) hydroxide Chemical compound [OH-].[OH-].[Fe+2] NCNCGGDMXMBVIA-UHFFFAOYSA-L 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 150000002739 metals Chemical class 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 1
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- BZHJMEDXRYGGRV-UHFFFAOYSA-N Vinyl chloride Chemical compound ClC=C BZHJMEDXRYGGRV-UHFFFAOYSA-N 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- 230000000996 additive effect Effects 0.000 description 1
- ANBBXQWFNXMHLD-UHFFFAOYSA-N aluminum;sodium;oxygen(2-) Chemical compound [O-2].[O-2].[Na+].[Al+3] ANBBXQWFNXMHLD-UHFFFAOYSA-N 0.000 description 1
- 239000010775 animal oil Substances 0.000 description 1
- 150000001450 anions Chemical class 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 239000011651 chromium Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 229910001882 dioxygen Inorganic materials 0.000 description 1
- 239000010840 domestic wastewater Substances 0.000 description 1
- 239000000839 emulsion Substances 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000007667 floating Methods 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000016615 flocculation Effects 0.000 description 1
- 229910002804 graphite Inorganic materials 0.000 description 1
- 239000010439 graphite Substances 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 239000002035 hexane extract Substances 0.000 description 1
- 239000002198 insoluble material Substances 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 239000010721 machine oil Substances 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- VLKZOEOYAKHREP-UHFFFAOYSA-N n-Hexane Chemical compound CCCCCC VLKZOEOYAKHREP-UHFFFAOYSA-N 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 235000019198 oils Nutrition 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 238000007790 scraping Methods 0.000 description 1
- 229910001388 sodium aluminate Inorganic materials 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 235000015112 vegetable and seed oil Nutrition 0.000 description 1
- 239000008158 vegetable oil Substances 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
Landscapes
- Water Treatment By Electricity Or Magnetism (AREA)
Description
本発明は汚濁物質の処理を効率よく行なうこと
のできる電気分解による廃水処理方法に関するも
のである。
廃水処理の一般的な手段として、陽極に鉄、ア
ルミニウム等の可溶性金属を用いて電解処理し、
電解作用によつて発生した金属イオンにより廃水
の汚濁物質を捕獲凝集してフロツクを生成させ、
同じく電解作用によつて発生した微細気泡をフロ
ツクに吸着させて分離浮上することは周知であ
る。しかしながら、従来から用いられている処理
装置においては、消耗した電極板の交換が必要で
あるとともに、電極板にスケールが付着して電導
性が低下した場合のスケール除去作業が困難であ
るなど、取扱いが面倒なものであつた。また電極
板の有効表面積を大きくするためには複数の陽極
と陰極を交互に配置するなどの必要があり、構造
が複雑になるとともに全体として大型になりやす
いという問題もあつた。
本発明はこのような問題点に着目し、簡単な構
成によつて汚濁物質の処理を効率的に行なうこと
のできる電気分解による廃水処理方法を提供する
ことを目的としてなされたものである。
すなわち、本発明は、下部に廃水の流入口を、
上部に廃水の流出口をそれぞれ備えた絶縁物から
なる缶体の内部に一対の電極を所定の間隔を隔て
て立設し、相互間に廃水の通過を妨げない間隙を
形成できる形状であつて、アルミニウムを主成分
とし、少なくとも鉄を数%含み、表面に酸化被膜
あるいは水酸化被膜を形成した充填材を缶体内に
充填し、電極間に直流電圧を印加しながら廃水を
流入口から送入し、廃水が充填材の間隙を通過す
る間に電解処理し、汚濁物質の分解、吸着、凝集
等を行なつてフロツク化することにより汚濁物質
を缶体上部に分離浮上させることを特徴としてい
る。
このように、本発明においては、表面に酸化被
膜あるいは水酸化被膜を形成した充填材を缶体内
に充填しており、充填材からその成分金属の水酸
化物、すなわち水酸化アルミニウムや水酸化鉄が
廃水中に供給され、しかも各充填材が反応して反
応面積が格段に拡大されるため水酸化物の供給は
十分になされ、また電解に伴なう発生ガスの量も
増大して汚濁物質のフロツク化と浮上が効率的に
行なわれるのである。充填材は表面が絶縁性の被
膜で覆われているため、充填材相互間や電極間が
短絡されることはなく、しかも充填材間を通過す
る廃水との十分な接触が保たれて反応は促進され
る。更に、充填材が消耗した場合にはわずらわし
い交換作業は不要で上から投入して補充するだけ
でよく、取扱いは極めて簡単である。こうして得
られたフロツクは缶体の上部においてかき取り、
あるいは周知の浮上分離槽を併用してここで分離
させてかき取る等の手段によつて除去すればよ
い。
次に、図示の一実施例により本発明を具体的に
説明する。
図において、1は缶体、2は缶体1の底部の支
持枠3に支持された一対の電極、4は缶体1の最
下部に設けられた廃水の流入口、5は缶体1の上
部に設けられた廃水の流出口、6は充填材、7は
缶体の最上部に設けられたかき取り機、8は送気
管である。
缶体1は例えば塩化ビニールやFRPなどの絶
縁物で作られた有底筒状の縦長のものである。電
極2は棒状のものであり、缶体1の内部に所定の
間隔を隔てて立設され、図示しない適宜の給電手
段によつて直流電源に接続されている。これらの
電極2としては、例えばグラフアイト等のカーボ
ン系の不溶性のものが用いられ、場合によつては
陽極側にアルミニウムまたは鉄系のものが用いら
れる。
充填材6としては、アルミニウムを主成分と
し、少なくとも鉄を数%含むものが用いられ、そ
の形状は各充填材相互間に廃水の通過を妨げない
間隙を形成できるような形状、一般的には球ある
いはこれに近い形状のものが適しており、予め表
面に酸化被膜あるいは水酸化被膜が化学処理によ
つて形成されている。具体的な例を示すと、製鉄
用の脱酸剤として一般に用いられているアルミシ
ヨツトと称するアルミニウム球が用いられる。こ
れは直径25mm程度、高さ15mm程度の丸みのある円
錐状鋳球であつて、入手が容易且つ安価であり、
表面積が大きく、廃水がその間隙を適度の乱流と
なつて通過し、またその成分はアルミニウム80%
以上、鉄3〜5%であり、その他微量の亜鉛、マ
グネシウム等を含み、本発明における充填材とし
て適したものの一つである。これを予め皮膜形成
処理し、缶体1内に投入して最上部を残して内部
に充填する。
このような構成において、廃水を流入口4から
送り込み、電極2に直流電圧を印加すると、廃水
が充填材6の間隙を上昇する間に廃水中の汚濁物
質は分解され、再凝集し、あるいは物質の種類に
よつては縮合されて析出する。廃水中に存在する
塩素イオンや硫酸根イオンは充填材6の表面の皮
膜物質と反応し、水酸化アルミニウムや水酸化鉄
が生成され、前記析出物との共有結合、吸着、包
含等が進行し、次第に不溶性のフロツクが形成さ
れ、更に陰極側で発生する水素ガスや陽極側で発
生する酸素ガスとも反応し、またガスを吸着して
見かけの比重が小さくなり、フロツク化した汚濁
物質は缶体1の上部に浮上する。充填材6は両性
元素であるアルミニウムが主成分であるので、各
電極2に周辺ではアノード反応またはカソード反
応によつてイオン濃度が高まり、また分散したア
ニオン、カチオンも電極2の周辺に移動し、反応
は一層促進される。このように、充填材6の表面
が反応促進に関与し、反応面積が拡大されて反応
は効率よく行なわれる。これらの反応を通じて充
填材6の表面の皮膜物質は消耗するが、同時に新
しい皮膜が形成され、水酸化物の補充がなされ
る。
廃水の種類によつては、流入口4から送り込む
前の工程において廃水に添加剤を添加する。この
添加剤は、塩素イオンや硫酸根イオン等の不足を
補つて前記の反応を促進する機能を有する塩類が
主として使用され、例えば、アルミニウム系や鉄
系の塩化物を汚濁物質の量及び質に応じて添加
し、廃水中の塩素イオンの不足を補うのである。
この添加剤の種類は個々の廃水ごとに予備実験等
によつて適切なものを選定する必要がある。例え
ば、有機系生活排水の場合には塩化アルミニウム
(AlCl3、6H2O)またはアルミン酸ソーダ
(NaAlO3)等が有効であり、適切な添加により
充填材6の消耗も低減される。
本発明に使用する缶体1、電極2の大きさは比
較的自由であるが、例えば缶体1として直径300
mmφ、高さ1m、電極2として直径50mmφ、、長
さ800mmのものを使用し、電極間隔250mm(中心距
離)で電圧DC15V、電流2〜3A程度とした場
合、1時間当り1トンの廃水を汚濁物質の除去率
80%以上で処理することが可能であつた。
こうして缶体1の上部に分離浮上したフロツク
は、かき取り機7によりかき取り、スカム流出口
9から取り出され、流出口5からは浄化された廃
水が流出する。かき取り機7は周知の回転形を用
いることができ、図中7aは回転羽根、7bはモ
ータである。またここでのフロツク回収が不十分
な場合には、流出口5の次に周知の浮上分離槽を
配置してここで完全回収をはかればよく、処理済
の廃水は適宜曝気処理を行なつて放流される。な
お、送気管8は空気を送り込んでフロツクに上昇
力を付与するためのものであり、上昇力が不足す
るような場合に使用して充填材6相互間の間隙が
詰まることを防止する。
以上の実施例の説明からも明らかなように、本
発明によれば、缶体内に充填された充填材から活
性化された水酸化物が廃水中に供給され、しかも
各充填材によつて反応面積が拡大されるため、汚
濁物質に対する反応が効率的に行なわれ、比較的
小型な装置で多量の廃水を処理することができる
のである。また本発明においては、充填材が消耗
した場合には必要量を上部から投入して補充する
だけでよく、保守管理が簡単で維持費を低減する
ことが可能である。なお、充填材の消耗は理論的
にはアボガトローの法則により計算されるが、実
際の消耗量は汚濁度、添加剤、電圧電流等によつ
て若干の変動があり、適切な添加剤の使用により
補充の頻度を少なくすることができる。
なお、本発明においては、必要となる電力量が
小さいため省エネルギーの観点からも有利であ
り、日中は太陽電池による運転も可能で、この点
からも維持費の低減が可能となる。
次に、本発明の廃水処理方法による処理結果の
実例を示す。
The present invention relates to a method for treating wastewater by electrolysis, which can efficiently treat pollutants. As a general means of wastewater treatment, electrolytic treatment is performed using soluble metals such as iron and aluminum for the anode.
The metal ions generated by electrolysis capture pollutants in wastewater and coagulate them to form flocs.
Similarly, it is well known that microbubbles generated by electrolytic action are adsorbed to flocs and floated separately. However, with conventional processing equipment, it is necessary to replace worn-out electrode plates, and it is difficult to remove scale when scale adheres to the electrode plate and reduces conductivity. It was a hassle. In addition, in order to increase the effective surface area of the electrode plate, it is necessary to alternately arrange a plurality of anodes and cathodes, which leads to the problem that the structure becomes complicated and the overall size tends to increase. The present invention has been made in view of these problems, and has an object to provide a wastewater treatment method using electrolysis that is simple in construction and capable of efficiently treating pollutants. That is, the present invention provides a wastewater inlet at the bottom,
A pair of electrodes are set upright at a predetermined distance apart inside a can made of an insulating material each having a wastewater outlet at the top, and the shape is such that a gap can be formed between them that does not impede the passage of wastewater. A filler whose main component is aluminum, contains at least a few percent iron, and has an oxide film or hydroxide film formed on the surface is filled into the can, and wastewater is introduced from the inlet while applying a DC voltage between the electrodes. The wastewater is electrolytically treated while it passes through the gaps in the filler, and the pollutants are decomposed, adsorbed, coagulated, etc. and turned into flocs, which separates and floats the pollutants to the top of the can. . In this way, in the present invention, the can body is filled with a filler having an oxide film or hydroxide film formed on the surface, and the hydroxides of the component metals, such as aluminum hydroxide and iron hydroxide, are extracted from the filler. is supplied to the wastewater, and each filler reacts, greatly expanding the reaction area, so hydroxide is supplied sufficiently, and the amount of gas generated due to electrolysis increases, causing pollutants. The flocculation and floating are performed efficiently. Since the surface of the filling material is covered with an insulating film, there is no short circuit between the filling materials or between the electrodes, and sufficient contact with the wastewater passing between the filling materials is maintained to prevent reactions. promoted. Furthermore, when the filling material is consumed, there is no need for troublesome replacement work, and it is only necessary to add it from above and replenish it, making it extremely easy to handle. The floc thus obtained is scraped off at the top of the can body,
Alternatively, the particles may be removed by means such as separating and scraping using a well-known flotation separation tank. Next, the present invention will be specifically explained with reference to an illustrated embodiment. In the figure, 1 is a can body, 2 is a pair of electrodes supported by a support frame 3 at the bottom of the can body 1, 4 is a wastewater inlet provided at the bottom of the can body 1, and 5 is a waste water inlet provided at the bottom of the can body 1. A waste water outlet is provided at the top, 6 is a filling material, 7 is a scraper provided at the top of the can body, and 8 is an air supply pipe. The can body 1 is a vertically elongated cylinder with a bottom made of an insulating material such as vinyl chloride or FRP. The electrodes 2 are rod-shaped, and are erected inside the can body 1 at predetermined intervals, and are connected to a DC power source by an appropriate power supply means (not shown). As these electrodes 2, carbon-based insoluble materials such as graphite are used, and in some cases, aluminum or iron-based materials are used on the anode side. As the filler 6, one whose main component is aluminum and contains at least a few percent of iron is used, and its shape is such that a gap can be formed between each filler without hindering the passage of waste water, generally. A sphere or similar shape is suitable, and an oxide film or hydroxide film is previously formed on the surface by chemical treatment. To give a specific example, an aluminum ball called an aluminum shot, which is generally used as a deoxidizing agent for iron manufacturing, is used. This is a rounded conical cast ball with a diameter of about 25 mm and a height of about 15 mm, and is easily available and inexpensive.
It has a large surface area, allowing wastewater to pass through the gap with moderate turbulence, and its composition is 80% aluminum.
The above content is 3 to 5% iron, and also contains trace amounts of zinc, magnesium, etc., and is one of the materials suitable as a filler in the present invention. This is preliminarily treated to form a film, and then put into the can body 1 and filled inside, leaving only the top part. In such a configuration, when wastewater is sent through the inlet 4 and a DC voltage is applied to the electrode 2, while the wastewater rises through the gaps in the filler 6, pollutants in the wastewater are decomposed, reagglomerated, or Depending on the type, it may be condensed and precipitated. The chloride ions and sulfate ions present in the wastewater react with the film material on the surface of the filler 6, producing aluminum hydroxide and iron hydroxide, which progress to covalent bonding, adsorption, inclusion, etc. with the precipitates. , an insoluble floc is gradually formed, and it also reacts with hydrogen gas generated on the cathode side and oxygen gas generated on the anode side, adsorbing gases and reducing the apparent specific gravity, and the floc-formed pollutants are absorbed into the can body. It floats to the top of 1. Since the filler 6 is mainly composed of aluminum, which is an amphoteric element, the ion concentration increases around each electrode 2 due to an anode reaction or a cathode reaction, and dispersed anions and cations also move to the periphery of the electrode 2. The reaction is further accelerated. In this way, the surface of the filler 6 participates in promoting the reaction, the reaction area is expanded, and the reaction is carried out efficiently. Through these reactions, the film material on the surface of the filler 6 is consumed, but at the same time a new film is formed and hydroxide is replenished. Depending on the type of wastewater, additives may be added to the wastewater in a process before it is sent through the inlet 4. These additives are mainly salts that have the function of accelerating the above reactions by compensating for deficiencies in chlorine ions and sulfate ions. It is added accordingly to compensate for the lack of chlorine ions in wastewater.
It is necessary to select an appropriate type of additive for each wastewater through preliminary experiments. For example, in the case of organic domestic wastewater, aluminum chloride (AlCl 3 , 6H 2 O) or sodium aluminate (NaAlO 3 ) is effective, and consumption of the filler 6 can be reduced by appropriate addition. The size of the can body 1 and the electrode 2 used in the present invention are relatively free, but for example, the can body 1 has a diameter of 300 mm.
mmφ, height 1m, diameter 50mmφ, length 800mm as electrode 2, electrode spacing 250mm (center distance), voltage DC 15V, current 2 to 3A, 1 ton of waste water per hour. Pollutant removal rate
It was possible to process at 80% or more. The flocs thus separated and floated to the top of the can body 1 are scraped off by a scraper 7 and taken out from the scum outlet 9, and the purified wastewater flows out from the outlet 5. A well-known rotary type scraper 7 can be used, and in the figure, 7a is a rotary blade, and 7b is a motor. In addition, if the floc recovery here is insufficient, a well-known flotation separation tank may be placed next to the outflow port 5 to ensure complete recovery, and the treated wastewater may be aerated as appropriate. It is released into the river. The air supply pipe 8 is for feeding air to give a lifting force to the flocs, and is used when the lifting force is insufficient to prevent the gaps between the fillers 6 from being clogged. As is clear from the description of the above embodiments, according to the present invention, activated hydroxide is supplied to wastewater from the filler filled in the can body, and moreover, each filler causes a reaction. Since the area is expanded, reactions against pollutants can be carried out efficiently, and a large amount of wastewater can be treated with a relatively small device. Further, in the present invention, when the filler is used up, it is only necessary to replenish the filler by adding the required amount from the top, thereby simplifying maintenance and reducing maintenance costs. Note that the amount of filler consumption is calculated theoretically using Avogatlow's law, but the actual amount of consumption varies slightly depending on the degree of pollution, additives, voltage and current, etc. The frequency of replenishment can be reduced. Note that the present invention is advantageous from the viewpoint of energy saving because the required amount of electric power is small, and operation using solar cells is also possible during the day, which also makes it possible to reduce maintenance costs. Next, examples of treatment results by the wastewater treatment method of the present invention will be shown.
【表】【table】
【表】【table】
【表】【table】
【表】【table】
【表】【table】
【表】 (実例7) 含油廃水(機械油及び動植物油エマルジヨン) ノルマルヘキサン抽出分 100%【table】 (Example 7) Oil-containing wastewater (machine oil and animal and vegetable oil emulsions) Normal hexane extract 100%
【表】
このように、各種の廃水において、BOD、
COD、SS、その他の含有成分についてほとんど
の場合90%以上の除去率を示し、また通常の処理
方法では除去が困難な重金属(クロム、水銀、カ
ドミウム、鉛等)及び燐等に対しても平均90%以
上の除去率を得ることができるのである。[Table] In this way, in various wastewaters, BOD,
It exhibits a removal rate of 90% or more for COD, SS, and other contained components in most cases, and also removes heavy metals (chromium, mercury, cadmium, lead, etc.) and phosphorus that are difficult to remove with normal treatment methods on average. It is possible to obtain a removal rate of over 90%.
図面は本発明の方法を実施するための廃水処理
装置の概略断面図である。
1……缶体、2……電極、4……流入口、5…
…流出口、6……充填材。
The drawing is a schematic cross-sectional view of a wastewater treatment device for carrying out the method of the invention. 1...Can body, 2...Electrode, 4...Inflow port, 5...
...Outlet, 6...Filling material.
Claims (1)
をそれぞれ備えた絶縁物からなる缶体の内部に一
対の電極を所定の間隔を隔てて立設し、相互間に
廃水の通過を妨げない間隙を形成できる形状であ
つて、アルミニウムを主成分とし、少なくとも鉄
を数%含み、表面に酸化被膜あるいは水酸化被膜
を形成した充填材を缶体内に充填し、電極間に直
流電圧を印加しながら廃水を流入口から送入し、
廃水が充填材の間隙を通過する間に電解処理し、
汚濁物質の分解、吸着、凝集等を行なつてフロツ
ク化することにより汚濁物質を缶体上部に分解浮
上させることを特徴とする電気分解による廃水処
理方法。1 A pair of electrodes are set up at a predetermined distance from each other inside a can made of an insulating material, which has a wastewater inlet at the bottom and a wastewater outlet at the top, and prevents the passage of wastewater between them. The can is filled with a filler whose main component is aluminum, contains at least a few percent of iron, and has an oxide film or hydroxide film formed on the surface, and a DC voltage is applied between the electrodes. while introducing wastewater from the inlet,
Electrolytic treatment is performed while the wastewater passes through the gaps in the filler,
A wastewater treatment method using electrolysis, characterized in that the pollutants are decomposed and floated to the upper part of the can body by decomposing, adsorbing, coagulating, etc. the pollutants and turning them into flocs.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4118783A JPS59166289A (en) | 1983-03-11 | 1983-03-11 | Treatment of waste water by electrolysis |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4118783A JPS59166289A (en) | 1983-03-11 | 1983-03-11 | Treatment of waste water by electrolysis |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS59166289A JPS59166289A (en) | 1984-09-19 |
| JPS6312678B2 true JPS6312678B2 (en) | 1988-03-22 |
Family
ID=12601408
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP4118783A Granted JPS59166289A (en) | 1983-03-11 | 1983-03-11 | Treatment of waste water by electrolysis |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS59166289A (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR100310272B1 (en) * | 1999-10-20 | 2001-11-14 | 박호군 | Electrochemical Wastewater Treatment System |
| CN103130308B (en) * | 2013-03-21 | 2013-12-11 | 东莞市珠江海咸水淡化研究所 | Electrochemical waste water treatment system and method for performing waste water treatment by using same |
| CN103241810B (en) * | 2013-05-31 | 2014-08-20 | 江苏大学 | Three-dimensional electrolysis waste water treatment device |
| CN112047444A (en) * | 2020-09-01 | 2020-12-08 | 中建环能科技股份有限公司 | Hydraulic mixing device |
-
1983
- 1983-03-11 JP JP4118783A patent/JPS59166289A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS59166289A (en) | 1984-09-19 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US3793173A (en) | Wastewater treatment using electrolysis with activated carbon cathode | |
| US6878268B2 (en) | Apparatus for purification of water | |
| CN206069598U (en) | A kind of wiring board ammonia nitrogen waste water electrochemical reactor processes complexes | |
| EP0480055B1 (en) | Method of purifying lacustrine water and filthy water purification boat | |
| JPH01168307A (en) | Method and apparatus for separating dispersion system in electrochemical cell into components | |
| CN110451697A (en) | Salt-containing organic wastewater electrocatalytic oxidation coupling pretreatment method and device | |
| KR100319022B1 (en) | Wastewater Treatment System Using Electrolytic Injury Method | |
| JPS6312678B2 (en) | ||
| KR20200134604A (en) | Water treatment apparatus using electric coagulation and floating method | |
| CN211284003U (en) | A compound integrated equipment of electric flocculation dissolved air flotation for waste water preliminary treatment | |
| CN210855619U (en) | Contain salt organic waste water electrocatalytic oxidation coupling preprocessing device | |
| CN105731696B (en) | Silicon carbide pickling waste water reclaiming treatment process | |
| CN107055709A (en) | A kind of method of use chalcopyrite Electrochemical Reactor with Three-dimensional Electrode Landfill Leachate | |
| CN118666374A (en) | Three-dimensional electric flocculation device for efficiently removing surface water phosphorus pollutants | |
| CN100464878C (en) | Electrokinetic Remediation of Contaminated Soil and Groundwater | |
| CN111362488B (en) | Electrochemical coagulation device and electrochemical water treatment system | |
| JPS637117B2 (en) | ||
| KR100466280B1 (en) | Suspended solid removing method of wastewater by electrofloatation and sedimentation | |
| CN107473527A (en) | A kind of method of Treatment of Oil/Water Emulsion by Electrolytic Flocculation | |
| WO1994011308A1 (en) | Method and device for purification of aqueous solutions by electroflotation | |
| JP4008248B2 (en) | Electrolytic water treatment equipment | |
| JPH08257568A (en) | Sewage treatment method and apparatus | |
| CN117383731B (en) | Treatment system and methods for oily wastewater in aluminum product manufacturing | |
| JP2000189973A (en) | Method for removing impurity by coagulation in water | |
| CN216337051U (en) | Complete process device for electrolyzing cyanide-containing wastewater by using packed bed |