JPH09314182A - Treatment process for selenium containing drain - Google Patents

Treatment process for selenium containing drain

Info

Publication number
JPH09314182A
JPH09314182A JP14038896A JP14038896A JPH09314182A JP H09314182 A JPH09314182 A JP H09314182A JP 14038896 A JP14038896 A JP 14038896A JP 14038896 A JP14038896 A JP 14038896A JP H09314182 A JPH09314182 A JP H09314182A
Authority
JP
Japan
Prior art keywords
selenium
drain
wastewater
tank
hexavalent
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.)
Withdrawn
Application number
JP14038896A
Other languages
Japanese (ja)
Inventor
Hiroyuki Hayashi
弘之 林
Tetsushi Noda
哲史 野田
Toshihiro Oshima
敏弘 大島
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.)
Chubu Electric Power Co Inc
Original Assignee
Chubu Electric Power Co Inc
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 Chubu Electric Power Co Inc filed Critical Chubu Electric Power Co Inc
Priority to JP14038896A priority Critical patent/JPH09314182A/en
Publication of JPH09314182A publication Critical patent/JPH09314182A/en
Withdrawn legal-status Critical Current

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  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide the good removing efficiency even when a hexavalent selenium compound is contained in drain and treat simply selenium containing drain by adding reducing bacteria in the selenium containing drain and reducing, adding a flocculant and/or a chelate agent into the drain and sedimentation separating a selenium content. SOLUTION: Selenium containing drain is introduced into a reduction tank 12, and the drain reduced in the reduction tank 12 is introduced into a flocculation reaction tank 14, and also introduced into a sedimentation separation tank 16 to flocculation separate a selenium compound. Thus even when a sexivalent selenium compound is contained, the removing efficiency is demonstrated in a good manner. The reason why the efficient removal of selenium can be carried out as above-mentioned is that the reduction of hexavalent selenium into tetravalent selenium becomes easier, which is considered to be difficult heretofore. A conventional flocculation separation tank can be utilized simply for the removing process.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、少なくとも六価セレン
化合物を含有するセレン含有排水の処理方法に関する。
FIELD OF THE INVENTION The present invention relates to a method for treating selenium-containing wastewater containing at least a hexavalent selenium compound.

【0002】[0002]

【従来の技術】工業的には、セレンは、特異な電気特性
を有しており、整流器、太陽電池、複写機感光体、赤色
顔料、触媒、ガラス着色剤等幅広い用途がある有用な元
素である。
BACKGROUND ART Industrially, selenium is a useful element having a wide range of uses such as rectifiers, solar cells, photoconductors for copying machines, red pigments, catalysts, and glass colorants because of its unique electrical characteristics. is there.

【0003】他方、健康影響に関して、セレンは、栄養
素として必須の元素と考えられており、ある種の癌に対
して保護作用を有することが示唆されている。しかし、
過剰のセレンを長く摂取した場合は、皮膚炎・中枢神経
系・胃腸に障害が発生する。さらに、セレンに発癌性の
疑いも持たれて来ている。(「米国暫定第1種飲料水規
制に対する無機物の処理技術−セレンの除去−」第28
頁参照、雑誌名:「水」1981年5月号、著者:足立
義雄、発行社:月刊“水”発行所) このため、わが国においても、米国公衆衛生協会基準に
倣って、平成6年2月に水質汚濁防止法施行令の一部が
改正され、セレン(許容限度0.1mg/L)が、排水
基準物質として新たな項目に加えられた。
On the other hand, regarding health effects, selenium is considered to be an essential element as a nutrient, and it has been suggested that it has a protective action against certain cancers. But,
Ingestion of excessive selenium for a long time causes dermatitis, central nervous system and gastrointestinal disorders. In addition, selenium has been suspected of being carcinogenic. ("Inorganic treatment technology for US provisional first-class drinking water regulation-selenium removal-", 28th
See page, Journal name: “Water” May 1981, Author: Yoshio Adachi, Publisher: Monthly “Water” publisher) Therefore, even in Japan, following the American Public Health Association standards, 1994 February A part of the Enforcement Ordinance of the Water Pollution Control Law was revised in March, and selenium (allowable limit 0.1 mg / L) was added to the new item as a wastewater standard substance.

【0004】従って、工業排水からのセレン化合物の簡
便な除去方法が希求されている。
Therefore, there is a need for a simple method for removing selenium compounds from industrial wastewater.

【0005】水中ではセレンは、亜セレン酸(SeO3
2- )(四価セレン化合物)又はセレン酸(SeO
4 2- )(六価セレン化合物)の二種類のみの形態で存在
し、共に酸性を呈する。このセレンの形態は両者とも安
定で酸化還元が起こりにくい。この存在形態の違いは、
セレン鉱物が水に溶解するときのpH、酸化還元雰囲気
で起こると考えられている。工業排水中では、発生源に
より存在形態が異なるものであると推察されている。
In water, selenium is selenous acid (SeO 3
2- ) (Tetravalent selenium compound) or Selenate (SeO
4 2- ) (hexavalent selenium compound) exists in only two forms, and both are acidic. Both forms of selenium are stable and are unlikely to undergo redox. The difference of this existence form is
It is believed that the selenium mineral dissolves in water at a pH and in a redox atmosphere. It is estimated that the form of existence in industrial wastewater varies depending on the source.

【0006】セレン含有排水の簡便な処理方法として
は、例えば、硫酸第二鉄を含む凝集剤を用いた凝集処理
方法によるセレンの除去方法がある(前記刊行物第31
頁第1段参照)。なお、イオン交換樹脂を使用する方法
も考えられるが、イオン交換樹脂は一般に高価であり、
かつ、大量処理には向かない。
[0006] As a simple method for treating selenium-containing wastewater, there is, for example, a method for removing selenium by a flocculation method using a flocculant containing ferric sulfate (Publication No. 31 above).
(See page 1st tier). Although a method using an ion exchange resin can be considered, the ion exchange resin is generally expensive,
Moreover, it is not suitable for mass processing.

【0007】[0007]

【発明が解決しようとする課題】しかし、上記従来の凝
集処理方法では、四価セレン化合物に対しては、除去率
が80%と高いが、六価セレン化合物に対しては、除去
率が10%と低い(前記刊行物第31頁第1段参照)。
However, in the above-mentioned conventional coagulation treatment method, the removal rate is as high as 80% for tetravalent selenium compounds, but the removal rate is 10% for hexavalent selenium compounds. % (See the above-mentioned publication page 31 column 1).

【0008】そこで、セレン含有排水中を還元剤を添加
して六価セレン化合物を還元処理を行うことが考えられ
る。
Therefore, it is conceivable to add a reducing agent to the selenium-containing wastewater to reduce the hexavalent selenium compound.

【0009】しかし、本発明者らが、硫酸第一鉄、塩化
第一鉄、亜硫酸水素ナトリウム、亜硫酸ナトリウム等の
汎用還元剤で還元・凝集処理しても、除去効率が良好で
ないことが分かった。
However, the present inventors have found that the removal efficiency is not good even if the reduction / aggregation treatment is performed with a general-purpose reducing agent such as ferrous sulfate, ferrous chloride, sodium bisulfite and sodium sulfite. .

【0010】本発明は、上記にかんがみて、六価セレン
化合物を含んでいても除去効率が良好で、しかも、除去
方法も簡便なセレン含有排水の処理方法を提供すること
を目的とする。
In view of the above, it is an object of the present invention to provide a method for treating selenium-containing wastewater which has a good removal efficiency even if it contains a hexavalent selenium compound and is simple in removal method.

【0011】[0011]

【課題を解決するための手段】本発明に係るセレン含有
排水の処理方法は、上記課題を、下記構成により解決す
るものである。
The method for treating selenium-containing wastewater according to the present invention solves the above problems by the following constitution.

【0012】少なくとも六価セレン化合物を含有するセ
レン含有排水の処理方法であって、セレン含有排水中に
還元バクテリアを添加して行う還元処理工程と、該排水
中に凝集剤及び/又はキレート剤を添加して、セレン成
分を沈殿分離させる凝集処理工程、とを含むことを特徴
とする。
[0012] A method for treating selenium-containing wastewater containing at least a hexavalent selenium compound, which comprises a reducing treatment step performed by adding reducing bacteria to the selenium-containing wastewater, and a coagulant and / or a chelating agent in the wastewater. And an aggregating treatment step of adding and precipitating and separating the selenium component.

【0013】[0013]

【手段の詳細な説明】次に、上記手段の各構成について
詳細な説明を行う。
[Detailed Description of Means] Next, each component of the above means will be described in detail.

【0014】(1) 本発明で使用される還元バクテリアと
しては、具体的には、ニトロバクター等を挙げることが
できる。
(1) Specific examples of the reducing bacteria used in the present invention include Nitrobacter and the like.

【0015】上記還元バクテリアの添加量は、還元バク
テリアの強度・種類に異なるが、例えば、ニトロバクタ
ーの場合、排水1m3 に対して40〜160L(望まし
くは、60〜100L)とする。
The amount of the reducing bacteria added varies depending on the strength and type of the reducing bacteria. For example, in the case of Nitrobacter, it is 40 to 160 L (preferably 60 to 100 L) per 1 m 3 of waste water.

【0016】添加量が40L/m3 未満では、還元バク
テリアの量が少なすぎて六価セレンが十分に還元され
ず、また、160L/m3 を越えても、それ以上の還元
作用の増大が余り期待できず無駄である。
If the amount added is less than 40 L / m 3 , the amount of reducing bacteria is too small to reduce hexavalent selenium sufficiently, and if it exceeds 160 L / m 3 , the reduction action is further increased. It is useless because we cannot expect much.

【0017】本発明で使用される凝集剤としては、硫酸
アルミニウム、ポリ塩化アルミニウム、塩化第一鉄、塩
化第二鉄、硫酸第一鉄、硫酸第二鉄、硫酸マグネシウ
ム、塩化マグネシウム、亜硫酸水素ナトリウム、亜硫酸
ナトリウム、等を挙げることができ、これらのうちから
一種または二種以上を選択することができる。特に塩化
第二鉄を含むものが望ましい。
The flocculant used in the present invention includes aluminum sulfate, polyaluminum chloride, ferrous chloride, ferric chloride, ferrous sulfate, ferric sulfate, magnesium sulfate, magnesium chloride, sodium hydrogen sulfite. , Sodium sulfite, and the like, and one or more of them can be selected from these. Those containing ferric chloride are particularly desirable.

【0018】また、本発明で使用されるキレート剤とし
ては、−NH−CS2 Na、−SNa等のキレート形成
基を備えた高分子重金属捕集剤を挙げることができる。
具体的には、「エポフロックL−1」(ミヨシ油脂製)
等を挙げることができる。
Examples of the chelating agent used in the present invention include polymeric heavy metal scavengers having a chelate forming group such as —NH—CS 2 Na and —SNa.
Specifically, "Epofloc L-1" (made by Miyoshi Yushi)
And the like.

【0019】なお、凝集剤及びキレート剤の混合物を使
用する場合、凝集剤/キレート剤の混合比は、5/2〜
5/1(望ましくは、3/1〜4/1)とする。
When a mixture of a coagulant and a chelating agent is used, the mixing ratio of coagulant / chelating agent is 5 / 2-
5/1 (desirably 3/1 to 4/1).

【0020】上記凝集剤及び/又はキレート剤の添加量
は、排水に含まれるセレンの全量に対して50〜800
倍量(望ましくは、200〜600倍量)とする。
The coagulant and / or chelating agent is added in an amount of 50 to 800 with respect to the total amount of selenium contained in the wastewater.
Double the amount (preferably 200 to 600 times the amount).

【0021】添加量が50倍量未満では、セレンを十分
に凝集・沈殿させることができず、また、800倍量を
越えた場合、過剰添加であり、それ以上セレン化合物の
凝集・沈殿が期待できず無駄である。
When the amount added is less than 50 times, the selenium cannot be sufficiently aggregated / precipitated, and when it exceeds 800 times, the selenium is excessively added and further aggregation and precipitation of the selenium compound is expected. It is useless because it cannot be done.

【0022】(2) 本発明のセレン含有排水の処理方法
は、具体的には、下記の如く行う(図1参照)。
(2) The method for treating selenium-containing wastewater of the present invention is specifically carried out as follows (see FIG. 1).

【0023】まず、還元槽12中にセレン含有排水を導
入し、該還元槽12で還元処理を経た排水を凝集反応槽
14に導入して、さらに、沈殿分離槽16に導入してセ
レン化合物の凝集分離処理を行う。
First, selenium-containing wastewater is introduced into the reduction tank 12, and the wastewater that has undergone the reduction treatment in the reduction tank 12 is introduced into the coagulation reaction tank 14 and further into the precipitation separation tank 16 to remove the selenium compound. Perform aggregation and separation processing.

【0024】なお、還元槽12は、硝化室18、脱窒室
20、酸化室22の三室に分かれており、主として、脱
窒室20で六価セレン化合物の還元処理が行われるもの
と推定される。
The reduction tank 12 is divided into three chambers, a nitrification chamber 18, a denitrification chamber 20, and an oxidation chamber 22, and it is presumed that the hexavalent selenium compound is mainly reduced in the denitrification chamber 20. It

【0025】[0025]

【発明の効果】本発明のセレン含有排水の処理方法は、
上記の如く、少なくとも六価セレン化合物を含有するセ
レン含有排水の処理方法であって、セレン含有排水中に
還元バクテリアを添加して行う還元処理工程と、該排水
中に凝集剤及び/又はキレート剤を添加して、セレン成
分を凝集分離させる凝集処理工程と、とを含むことを特
徴とする構成により、下記効果を奏するものである。
The method for treating selenium-containing wastewater of the present invention comprises:
As described above, a method for treating selenium-containing wastewater containing at least a hexavalent selenium compound, the reduction treatment step being carried out by adding reducing bacteria to the selenium-containing wastewater, and a coagulant and / or a chelating agent in the wastewater. And a coagulation treatment step in which the selenium component is coagulated and separated, and a constitution characterized by including the following effects.

【0026】本発明のセレン含有排水の処理方法は、後
述の実施例で支持される如く、六価セレン化合物を含ん
でいても除去効率が良好で、しかも、除去方法も、従来
の凝集分離槽を利用でき簡便である。 効率的なセレン
除去が可能となった理由は、従来困難視されていた六価
セレンの四価セレンへの還元が、還元性バクテリアによ
り容易になったためである。
The selenium-containing wastewater treatment method of the present invention has good removal efficiency even when it contains a hexavalent selenium compound, and the removal method is the same as that of the conventional coagulation / separation tank, as supported by the examples described later. Can be used and is simple. The reason why efficient removal of selenium is possible is that reduction of hexavalent selenium to tetravalent selenium, which has been difficult in the past, is facilitated by reducing bacteria.

【0027】[0027]

【実施例】以下、本発明の効果を確認するために行った
実施例(図1に示す実機試験)について説明をする。
EXAMPLE An example (actual machine test shown in FIG. 1) carried out to confirm the effect of the present invention will be described below.

【0028】<実施例1>図1において、セレン全量が
0.19mg/Lであるセレン含有排水を、還元槽12
(ニトロバクター添加量:80L/m3 )に導入し、還
元処理(処理時間:2時間)後、該排水を、凝集反応槽
14(凝集剤添加量:硫酸アルミニウム/塩化第二鉄
(混合比2/1)の混合物100mg/L)に導入し、凝
集反応処理(処理時間:約10分)を行い、さらに、沈
殿分離槽16に導入して沈殿分離処理(処理時間:約1
時間)を行う。
<Example 1> In FIG. 1, selenium-containing wastewater containing 0.19 mg / L of selenium in the reducing tank 12
(Nitrobacter addition amount: 80 L / m 3 ) and after reduction treatment (treatment time: 2 hours), the waste water was treated with the flocculation reaction tank 14 (flocculant addition amount: aluminum sulfate / ferric chloride (mixing ratio). 2/1) mixture (100 mg / L) and subjected to a flocculation reaction treatment (treatment time: about 10 minutes), and further introduced into a precipitation separation tank 16 to perform a precipitation separation treatment (treatment time: about 1 minute).
Time).

【0029】このときの、還元槽の入口及び出口、沈殿
分離槽の出口における排水のセレン全量及び六価セレ
ン、四価セレンの量を測定した。その結果を示す表1か
ら、本実施例における、排水中のと六価セレンの含有率
が高い(六価セレン/四価セレン=2/15)にもかか
わらず、セレン除去効率が、全体で約80%と高いこと
が分かる。
At this time, the total amount of selenium and the amount of hexavalent selenium and tetravalent selenium in the wastewater at the inlet and outlet of the reduction tank and the outlet of the precipitation separation tank were measured. From Table 1 showing the results, although the content ratio of hexavalent selenium in the waste water is high (hexavalent selenium / tetravalent selenium = 2/15) in this example, the selenium removal efficiency is high as a whole. It turns out that it is as high as about 80%.

【0030】[0030]

【表1】 [Table 1]

【0031】<実施例2>実施例1において、セレン含
有排水として、セレン全量が0.23mg/Lであるもの
を使用して、ニトロバクターを80L/m3 添加し、凝
集反応槽に塩化第二鉄(凝集剤)60mg/L及びキレー
ト剤:「エポフロックL−1」20mg/Lを添加した以
外は、同様に排水処理を行った。
<Example 2> In Example 1, the selenium-containing wastewater having a total selenium content of 0.23 mg / L was used, and 80 L / m 3 of nitrobacter was added to the coagulation reaction tank. Waste water treatment was performed in the same manner except that diiron (coagulant) 60 mg / L and chelating agent: "Epofloc L-1" 20 mg / L were added.

【0032】実施例1と同様にして測定した結果を表2
に示すが、本実施例における、排水中の六価セレンの含
有率が高い(六価セレン/四価セレン=9/1)にもか
かわらず、セレン除去効率が、全体で約75%と高いこ
とが分かる。
The results measured in the same manner as in Example 1 are shown in Table 2.
Although the content of hexavalent selenium in the wastewater is high (hexavalent selenium / tetravalent selenium = 9/1) in this example, the selenium removal efficiency is as high as about 75% as a whole. I understand.

【0033】[0033]

【表2】 [Table 2]

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

【図1】本発明において使用されるセレン含有排水処理
装置
FIG. 1 Sewage treatment equipment containing selenium used in the present invention

【符号の説明】[Explanation of symbols]

12 還元槽 14 凝集反応槽 16 沈殿分離槽 18 硝化室 20 脱窒室 22 酸化室 12 reduction tank 14 aggregation reaction tank 16 precipitation separation tank 18 nitrification chamber 20 denitrification chamber 22 oxidation chamber

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 少なくとも六価セレン化合物を含有する
セレン含有排水の処理方法であって、 前記セレン含有排水中に還元作用を有するバクテリア
(以下「還元バクテリア」)を添加して行う還元処理工
程と、 該排水中に凝集剤及び/又はキレート剤を添加して、セ
レン成分を凝集分離させる凝集処理工程、 とを含むことを特徴とするセレン含有排水の処理方法。
1. A method for treating selenium-containing wastewater containing at least a hexavalent selenium compound, wherein a reduction treatment step is performed by adding bacteria having a reducing action (hereinafter referred to as “reducing bacteria”) to the selenium-containing wastewater. A coagulation treatment step of coagulating and separating a selenium component by adding a coagulant and / or a chelating agent to the wastewater, and a method for treating selenium-containing wastewater.
【請求項2】 請求項1において、前記還元バクテリア
が、ニトロバクターであることを特徴とするセレン含有
排水の処理方法。
2. The method for treating selenium-containing wastewater according to claim 1, wherein the reducing bacterium is Nitrobacter.
【請求項3】 請求項2において、前記ニトロバクター
の排水中の添加量が、40〜160L/m3 であること
を特徴とするセレン含有排水の処理方法。
3. The method for treating selenium-containing wastewater according to claim 2, wherein the amount of nitrobacter added to the wastewater is 40 to 160 L / m 3 .
【請求項4】 請求項3において、前記凝集剤が塩化第
二鉄を含むものであり、該塩化第二鉄の凝集剤としての
添加量が40〜150mg/Lであることを特徴とする
セレン含有排水の処理方法。
4. The selenium according to claim 3, wherein the coagulant contains ferric chloride, and the amount of the ferric chloride added as a coagulant is 40 to 150 mg / L. Treatment method of contained wastewater.
【請求項5】 請求項1において、前記凝集剤が塩化第
二鉄を含むものであることを特徴とするセレン含有排水
の処理方法。
5. The method for treating selenium-containing wastewater according to claim 1, wherein the coagulant contains ferric chloride.
【請求項6】 請求項2において、前記凝集剤が塩化第
二鉄を含むものであり、該塩化第二鉄の凝集剤としての
添加量が40〜150mg/Lであることを特徴とする
セレン含有排水の処理方法。
6. The selenium according to claim 2, wherein the coagulant contains ferric chloride, and the amount of the ferric chloride added as a coagulant is 40 to 150 mg / L. Treatment method of contained wastewater.
JP14038896A 1996-06-03 1996-06-03 Treatment process for selenium containing drain Withdrawn JPH09314182A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP14038896A JPH09314182A (en) 1996-06-03 1996-06-03 Treatment process for selenium containing drain

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP14038896A JPH09314182A (en) 1996-06-03 1996-06-03 Treatment process for selenium containing drain

Publications (1)

Publication Number Publication Date
JPH09314182A true JPH09314182A (en) 1997-12-09

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JP14038896A Withdrawn JPH09314182A (en) 1996-06-03 1996-06-03 Treatment process for selenium containing drain

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008012461A (en) * 2006-07-07 2008-01-24 Central Res Inst Of Electric Power Ind Method for treating selenic acid compound-containing liquid using microorganism
JP2012192359A (en) * 2011-03-17 2012-10-11 Central Research Institute Of Electric Power Industry Selenium containing water reduction treatment apparatus and selenium containing water reduction treatment method
JP2019026521A (en) * 2017-08-01 2019-02-21 宇部興産株式会社 Method for producing potassium chloride salt
JP2019171291A (en) * 2018-03-28 2019-10-10 栗田工業株式会社 Method and apparatus for treating selenium-containing water

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008012461A (en) * 2006-07-07 2008-01-24 Central Res Inst Of Electric Power Ind Method for treating selenic acid compound-containing liquid using microorganism
JP2012192359A (en) * 2011-03-17 2012-10-11 Central Research Institute Of Electric Power Industry Selenium containing water reduction treatment apparatus and selenium containing water reduction treatment method
JP2019026521A (en) * 2017-08-01 2019-02-21 宇部興産株式会社 Method for producing potassium chloride salt
JP2019171291A (en) * 2018-03-28 2019-10-10 栗田工業株式会社 Method and apparatus for treating selenium-containing water

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