JP2548096B2 - Method of treating wastewater containing cadmium - Google Patents

Method of treating wastewater containing cadmium

Info

Publication number
JP2548096B2
JP2548096B2 JP62259080A JP25908087A JP2548096B2 JP 2548096 B2 JP2548096 B2 JP 2548096B2 JP 62259080 A JP62259080 A JP 62259080A JP 25908087 A JP25908087 A JP 25908087A JP 2548096 B2 JP2548096 B2 JP 2548096B2
Authority
JP
Japan
Prior art keywords
cadmium
wastewater containing
containing cadmium
precipitate
neutralization
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 - Fee Related
Application number
JP62259080A
Other languages
Japanese (ja)
Other versions
JPH0199688A (en
Inventor
津良 塩見
勉丈 福田
孝博 金平
泰崇 中村
英治 松嶋
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.)
DOWA KOEI KK
Original Assignee
DOWA KOEI 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 DOWA KOEI KK filed Critical DOWA KOEI KK
Priority to JP62259080A priority Critical patent/JP2548096B2/en
Publication of JPH0199688A publication Critical patent/JPH0199688A/en
Application granted granted Critical
Publication of JP2548096B2 publication Critical patent/JP2548096B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Landscapes

  • Removal Of Specific Substances (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 この発明は鉱山廃水や工場廃液のように、鉄、銅、
鉛、アルミニウムの外に、特に亜鉛やカドミウムを含む
廃水の合理的、経済的な処理方法に関する。
DETAILED DESCRIPTION OF THE INVENTION [Industrial field of application] The present invention is applicable to iron, copper, mining wastewater and industrial wastewater.
The present invention relates to a rational and economical treatment method for wastewater containing lead, aluminum, and especially zinc and cadmium.

〔従来の技術及びその問題点〕[Conventional technology and its problems]

従来から、カドミウムを含む廃水の処理手段としては
種々の方法が利用されているが、中でも廃水中に苛性ソ
ーダや消石灰、或いは炭酸ソーダを相当量添加し、廃水
中の重金属を水酸化物として沈降分離する方法が最も一
般的であった。
Conventionally, various methods have been used as a means for treating wastewater containing cadmium, but among them, caustic soda, slaked lime, or sodium carbonate is added to the wastewater in a considerable amount, and heavy metals in the wastewater are precipitated and separated as hydroxides. The most common method was to

しかしこの場合、カドミウムを排水基準の0.1mg/l以
下に保持するにはpHを10.5以上にする必要があったか
ら、上記苛性ソーダ、消石灰または炭酸ソーダ等の薬剤
費が高くなる上、pHを10.5とした処理水を排水基準のpH
8.6以下にするために逆中和が必要となり、その為の逆
中和設備の建設や硫酸など中和剤の消費が避けられなか
ったのである。
However, in this case, in order to keep the cadmium at 0.1 mg / l or less of the drainage standard, it was necessary to set the pH to 10.5 or higher, so the cost of the chemicals such as caustic soda, slaked lime or sodium carbonate becomes high, and the pH was set to 10.5. The treated water is treated as a drainage standard pH
Reverse neutralization was necessary in order to achieve 8.6 or less, and the construction of reverse neutralization equipment and the consumption of neutralizing agents such as sulfuric acid were unavoidable for that purpose.

更にこの処理法によれば、pH10.5で再溶解したアルミ
ニウム等がpH8.6に逆中和される際に析出し、その処理
等も必要となる他、沈澱した水酸化物の安定容積が極め
て大きく(40%)、いきおい脱水費用が嵩むなど種々の
問題点が見られたものである。
Furthermore, according to this treatment method, aluminum etc. redissolved at pH 10.5 precipitates when it is reverse-neutralized to pH 8.6, and the treatment etc. is required, and the stable volume of the precipitated hydroxide is It was extremely large (40%), and various problems such as high dehydration cost were observed.

〔問題点を解決するための手段〕[Means for solving problems]

このような事情に鑑み、本発明者らは鋭意、実験研究
を重ねた結果、カドミウム等を含む重金属溶存廃水を、
まず炭酸カルシウムで中和することにより、廃液中に溶
存する鉄、銅、鉛、アルミニウムの略、全量および亜鉛
の大部分が沈降して液中から除かれると同時に、生成さ
れた沈澱物は、その安定容積が苛性ソーダ等の薬剤によ
る場合の澱物の安定容積の数分の1に止まり、脱水性が
極めて良好であるという事実を究明した。
In view of such circumstances, the present inventors have earnestly conducted experimental research, and as a result, have analyzed heavy metal-dissolved wastewater containing cadmium,
First, by neutralizing with calcium carbonate, almost all of iron, copper, lead, and aluminum dissolved in the waste liquid and most of zinc are precipitated and removed from the liquid, and at the same time, the generated precipitate is It was clarified that the stable volume was only a fraction of the stable volume of the starch when a chemical such as caustic soda was used, and the dehydratability was extremely good.

しかし上記中和液中には未だ亜鉛、カドミウムが残留
するので、その液中に更に苛性ソーダ等を加えてpH8〜
8.6にpH調整することにより、上記亜鉛の全量及びカド
ミウムの大部分を沈澱させ、なお該液中に残留する僅か
なカドミウムの除去に対しては、前記pH調整によって生
成した沈澱物を固液分離した上で、その上澄水中に少量
のキレート樹脂またはキレート剤を添加して、これを補
促するようにし、上記廃水のpH並びに溶存するすべての
重金属を排水基準以下に抑えた処理水を経済的に得るこ
とに成功したものである。
However, since zinc and cadmium still remain in the neutralizing solution, caustic soda is added to the solution to adjust the pH to 8
By adjusting the pH to 8.6, the total amount of zinc and most of the cadmium was precipitated, and in order to remove a small amount of cadmium remaining in the solution, the precipitate produced by the pH adjustment was subjected to solid-liquid separation. In addition, a small amount of chelating resin or chelating agent is added to the supernatant water to promote this, and the treated water in which the pH of the wastewater and all dissolved heavy metals are kept below the wastewater standard is economical. It has succeeded in getting it.

尚、この場合、pH調整後に固液分離された上澄水中の
カドミウムは極めて微量であるので、キレート剤の消費
は極めて少量である。
In this case, since the amount of cadmium in the supernatant water separated by solid-liquid separation after pH adjustment is extremely small, the consumption of the chelating agent is extremely small.

以上要するに本発明の処理方法は、先ずカドミウムを
含む廃水を炭酸カルシウムによってpH6程度に中和し、
次に該中和液を苛性ソーダによってpH8〜8.6に調整す
る。
In short, the treatment method of the present invention is to neutralize the wastewater containing cadmium with calcium carbonate to a pH of about 6,
Next, the neutralized solution is adjusted to pH 8 to 8.6 with caustic soda.

これによって生成された沈澱物を固液分離した後、そ
の上澄水中に僅かに残留するカドミウムをキレート剤等
によって補促することを特徴としたカドミウムを含む廃
水の処理方法である。
This is a method for treating wastewater containing cadmium, characterized in that after solid-liquid separation of the precipitate generated by this, cadmium slightly remaining in the supernatant water is promoted by a chelating agent or the like.

〔作用〕[Action]

叙上の処理方法によれば、廃水中和の際、鉄、銅、
鉛、アルミニウム等の化合酸によって、その大部分が消
費されるアルカリ量を安価な炭酸カルシウムに置換し、
苛性ソーダ等のアルカリ剤を亜鉛とカドミウムの沈澱除
去に利用するようにしたことにより、主として薬剤価格
の低減並びに生成沈澱物の安定容積の減少を計り得ると
いう顕著な作用を奏するものである。
According to the above treatment method, iron, copper,
By compounding acids such as lead and aluminum, replace most of the consumed alkaline amount with inexpensive calcium carbonate,
By using an alkaline agent such as caustic soda for the removal of zinc and cadmium precipitates, it is possible to achieve a remarkable effect mainly in reducing the drug price and the stable volume of the formed precipitate.

〔実施例〕〔Example〕

以下、本発明方法を一つの実施例に従って更に具体的
に述べと、使用した試験装置は容量16lの中和槽からな
る通常の曝気式中和装置であり、また処理原液としては
鉄20mg/l、銅250mg/l、アルミニウム230mg/l、亜鉛350m
g/lおよびカドミウム10mg/lを含むpH3.5の人工廃水を使
用した。
Hereinafter, the method of the present invention will be described more specifically according to one embodiment.The test apparatus used was a normal aeration type neutralization apparatus consisting of a neutralization tank having a capacity of 16 l, and the stock solution for treatment was iron 20 mg / l. , Copper 250mg / l, aluminum 230mg / l, zinc 350m
An artificial wastewater of pH 3.5 containing g / l and 10 mg / l of cadmium was used.

この処理原液10lを上記曝気式中和槽に投入し、先ず
炭カル粉2460mg/lを添加して12.6l/minの空気量で60分
間曝気攪拌してpH6.3とし(中和工程)、上記原液中に
溶存する鉄、銅、アルミニウムの大部分及び亜鉛の相当
量を沈澱させる。
This treatment stock solution 10l was charged into the aeration-type neutralization tank, and firstly, calcium carbonate powder 2460mg / l was added and aerated and stirred at an air amount of 12.6l / min for 60 minutes to pH 6.3 (neutralization step), Most of the iron, copper, aluminum and zinc dissolved in the stock solution are precipitated.

次いで、上記沈澱物をそのまゝの状態で苛性ソーダ40
0mg/lを加えて10分間攪拌し、pHを8.44とした(pH調整
工程)。この場合、鉄、銅、アルミニウムは勿論、前記
中和工程で比較的多量に残存していた亜鉛のほゞ全量と
カドミウムの大部分の沈降が見られた。こゝで中和槽内
の固液を分離し、その沈澱物はこれを取り出して脱水後
棄却するのであるが、この場合の沈澱物の安定容積(24
時間後)は8%で前に述べた従来の一般的処理法による
最終沈澱物の安定容積40%に比較して5分の1の値とな
り、これにより脱水性の大幅な向上が期待出来るのであ
る。
Then, the above precipitate is left as it is in a caustic soda 40
The pH was adjusted to 8.44 by adding 0 mg / l and stirring for 10 minutes (pH adjusting step). In this case, not only iron, copper, and aluminum but also a large amount of zinc, which remained in a relatively large amount in the neutralization step, and most of cadmium were precipitated. Here, the solid-liquid in the neutralization tank is separated, and the precipitate is taken out, dehydrated and discarded. In this case, the stable volume of the precipitate (24
(After time) is 8%, which is one fifth of the stable volume of the final precipitate obtained by the conventional general treatment method described above, which is 40%, which is expected to greatly improve the dehydration property. is there.

他方、上記固液分離によって得られた上澄水には、更
にキレート剤(例えば商標名「アロンキレートS−1」
東亜合成化学工業製)を5mg/l添加して5分間攪拌し
(キレート処理工程)、これを砂濾過槽を通して急速濾
過(濾過工程)したところ、該処理水のpH8.40、鉄0.01
mg/l、銅0.01mg/l、アルミニウム0.3mg/l、亜鉛0.11mg/
l、カドミウム0.006mg/lとなり、特にカドミウムの排水
基準0.1mg/lを大きく下廻る処理水を得たものである
(表−1参照)。
On the other hand, in the supernatant water obtained by the solid-liquid separation, a chelating agent (for example, trade name "Aron chelate S-1") is added.
(Toagosei Kagaku Kogyo Co., Ltd.) was added at 5 mg / l and stirred for 5 minutes (chelation process), and this was rapidly filtered through a sand filtration tank (filtration process).
mg / l, copper 0.01 mg / l, aluminum 0.3 mg / l, zinc 0.11 mg / l
l, cadmium was 0.006 mg / l, and in particular, treated water was obtained that was well below the cadmium drainage standard of 0.1 mg / l (see Table-1).

表−1 尚、上記実施例における試験結果を同一の人工原液を使
用して行った従来方法による試験結果と比較して上掲の
表−1に示す。
Table-1 The test results in the above examples are shown in Table 1 above in comparison with the test results by the conventional method performed using the same artificial undiluted solution.

〔発明の効果〕〔The invention's effect〕

以上、本発明の方法によれば、中和澱物の安定容積が
従来法の数分の1と極めて小さく、その結果として脱水
性の良い沈澱物とすることが出来るので、脱水設備及び
脱水費が大幅に節減出来る。
As described above, according to the method of the present invention, the stable volume of the neutralized precipitate is extremely small, which is a fraction of that of the conventional method, and as a result, a precipitate having good dehydration property can be obtained. Can be significantly reduced.

更に又、大部分の中和を安価な炭酸カルシウムによる
低pH中和としたゝめ、逆中和を行わずに済むので従来方
法に比較して逆中和による酸の消費と、その際に生成さ
れるアルミニウム沈澱物の処理等を不要として、全体的
な沈澱物の処理費や中和剤費の著しい節減が可能となる
等、その合理性、経済的効果は極めて顕著である。
Furthermore, most of the neutralization is done by low pH neutralization with inexpensive calcium carbonate, and reverse neutralization is not required. The rationality and economic effects are extremely remarkable, for example, the treatment of the produced aluminum precipitate is not required and the overall treatment cost of the precipitate and the cost of the neutralizing agent can be remarkably reduced.

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】カドミウムを含む廃水を曝気下において、
炭酸カルシウムによりpH6程度にする中和工程と、該中
和水を苛性ソーダによりpH8〜8.6にするpH調整工程を経
て生成された水酸化物を沈澱させる固液分離工程と、該
工程で得られた上澄水をキレート剤に吸着させるキレー
ト処理工程と、該液を濾過する濾過工程とからなるカド
ミウムを含む廃水の処理方法。
1. Aeration of wastewater containing cadmium,
A neutralization step of adjusting the pH to about 6 with calcium carbonate, a solid-liquid separation step of precipitating hydroxide produced through a pH adjusting step of adjusting the neutralized water to pH 8 to 8.6 with caustic soda, and the step obtained A method for treating wastewater containing cadmium, comprising a chelation treatment step of adsorbing supernatant water to a chelating agent and a filtration step of filtering the liquid.
JP62259080A 1987-10-13 1987-10-13 Method of treating wastewater containing cadmium Expired - Fee Related JP2548096B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP62259080A JP2548096B2 (en) 1987-10-13 1987-10-13 Method of treating wastewater containing cadmium

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP62259080A JP2548096B2 (en) 1987-10-13 1987-10-13 Method of treating wastewater containing cadmium

Publications (2)

Publication Number Publication Date
JPH0199688A JPH0199688A (en) 1989-04-18
JP2548096B2 true JP2548096B2 (en) 1996-10-30

Family

ID=17329037

Family Applications (1)

Application Number Title Priority Date Filing Date
JP62259080A Expired - Fee Related JP2548096B2 (en) 1987-10-13 1987-10-13 Method of treating wastewater containing cadmium

Country Status (1)

Country Link
JP (1) JP2548096B2 (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07100154B2 (en) * 1988-01-11 1995-11-01 川崎製鉄株式会社 Control method for waste liquid treatment equipment containing heavy metals
JP5246678B2 (en) * 2007-04-17 2013-07-24 太平洋セメント株式会社 Soil cleaning wastewater treatment method
JP2010099552A (en) * 2008-10-21 2010-05-06 Mitsubishi Materials Techno Corp Wastewater treatment method
JP5136800B2 (en) * 2009-04-02 2013-02-06 住友金属鉱山株式会社 Method for separating cadmium from aqueous solution
JP5985959B2 (en) * 2012-11-07 2016-09-06 水ing株式会社 Method and apparatus for treating waste liquid containing heavy metal

Also Published As

Publication number Publication date
JPH0199688A (en) 1989-04-18

Similar Documents

Publication Publication Date Title
US7033507B2 (en) Method for removing metals from acid mine drainage
JP3625270B2 (en) Waste disposal method
JP4374636B2 (en) Treatment method of waste liquid containing heavy metal complex
JP2548096B2 (en) Method of treating wastewater containing cadmium
JP4293520B2 (en) Fluorine ion removal method and remover
JP3325689B2 (en) Treatment method for metal-containing wastewater
JP2004050096A (en) Method for treating wastewater containing harmful substance without producing sludge, and chemical agent used therein
KR100259563B1 (en) Method for treating waste water containing heavy metal using material containing calsium, magnesium
JP3049851B2 (en) Treatment method for wastewater containing selenium
JP3334786B2 (en) Treatment method for wastewater containing insoluble and soluble lead, chromium and zinc
JPS61192386A (en) Treatment of waste water containing heavy metal complex
JP4039820B2 (en) Wastewater treatment method
JP3186094B2 (en) Treatment method for wastewater containing heavy metals
JP4014032B2 (en) Disposal method of wastewater containing dissolved copper complex compound and chemical used therefor
JP2910346B2 (en) Treatment method for wastewater containing heavy metals
JP2923212B2 (en) Wastewater treatment method
JP3788782B2 (en) Method for removing and recovering copper by treating waste water and chemicals used therefor
JP3632226B2 (en) Method for treating metal-containing wastewater
JP2004000963A (en) Treatment method of boron-containing drainage, and medicament used for the same
JP3493603B2 (en) Method for treating copper chloride-containing etching waste liquid, treatment agent, and method for recovering copper
JP3733452B2 (en) Waste disposal method
JP3282452B2 (en) How to remove selenium from wastewater
JP4110295B2 (en) Method for simultaneously treating copper etching waste liquid and resist waste liquid and chemicals used therefor
JP7240577B2 (en) Method for treating etching wastewater containing copper ions and water-soluble organic substances
JPH01249187A (en) Method for purifying waste containing gallium and arsenic

Legal Events

Date Code Title Description
LAPS Cancellation because of no payment of annual fees