JP2000202461A - Treatment of heavy metal complex-containing waste liquid - Google Patents

Treatment of heavy metal complex-containing waste liquid

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Publication number
JP2000202461A
JP2000202461A JP11004424A JP442499A JP2000202461A JP 2000202461 A JP2000202461 A JP 2000202461A JP 11004424 A JP11004424 A JP 11004424A JP 442499 A JP442499 A JP 442499A JP 2000202461 A JP2000202461 A JP 2000202461A
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JP
Japan
Prior art keywords
heavy metal
treatment
metal complex
added
iron
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.)
Granted
Application number
JP11004424A
Other languages
Japanese (ja)
Other versions
JP4374636B2 (en
Inventor
Minoru Watanabe
実 渡辺
Isamu Kato
勇 加藤
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Kurita Water Industries Ltd
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Kurita Water Industries Ltd
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Priority to JP00442499A priority Critical patent/JP4374636B2/en
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Anticipated expiration legal-status Critical
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Abstract

PROBLEM TO BE SOLVED: To efficiently separate heavy metal with less use quantity of chemical and to unnecessitate neutralization after the treatment, since the treatment enables at a lower pH region. SOLUTION: In this treatment method, a magnesium compound more than a reaction equivalent with respect to the heavy metal complex is added to the waste water containing heavy metal complex, and besides 50-5000 mg/l of an iron- and/or an aluminum compound are added, and the solid is separated from the solution at pH 5.5-9.5. Thus, the heavy metal can be efficiently separated with less chemical use quantity, and neutralization after the treatment is unnecessary and a synergetic effect can be obtained compared to separate treatments of respective compounds.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は重金属錯体を含む排
水から重金属を分離する処理方法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 for separating heavy metals from wastewater containing heavy metal complexes.

【0002】[0002]

【従来の技術】キレート剤を含む重金属排水は重金属が
錯体を形成していて処理が困難である。従来、重金属錯
体を含む排水の処理としては、消石灰、塩化カルシウム
等のカルシウム塩を添加してアルカリ性で凝集沈殿処理
する方法、塩化鉄、硫酸鉄等の鉄塩を添加してアルカリ
性で凝集沈殿する方法、あるいはジエチルカルバミン酸
塩系等の重金属捕集剤と鉄またはアルミニウム塩を併用
する方法などがある。しかしながら、以上のような処理
方法は処理効率が悪く、キレート剤の種類によっては効
果がない場合があること、鉄塩が処理水中に残留する場
合があることなどの問題点がある。
2. Description of the Related Art Heavy metal wastewater containing a chelating agent is difficult to treat because heavy metals form a complex. Conventionally, as a treatment of wastewater containing a heavy metal complex, a method of adding calcium salts such as slaked lime and calcium chloride to carry out coagulation precipitation treatment, and adding iron salts such as iron chloride and iron sulfate to carry out coagulation precipitation. Or a method in which a heavy metal collector such as diethylcarbamate is used in combination with an iron or aluminum salt. However, the above-described treatment methods have problems in that the treatment efficiency is low, there are cases where there is no effect depending on the type of chelating agent, and there are cases where iron salts may remain in the treated water.

【0003】このような点を改善する処理方法として、
重金属錯体を含む排水にマグネシウム化合物を添加しp
H10〜12で固液分離する方法が提案されている(特
開昭61−192386号)。この方法は前記方法に比
べれば少ない薬剤使用量で効率よく重金属を分離でき、
重金属およびキレート剤の種類に関係なく、安定した処
理を行うことができる。しかしながら高pH領域で処理
するため、pH調整するためのアルカリ剤を多量に必要
とし、また放流するために再度酸で中和する必要が生
じ、必ずしも効率的とはいえない。
[0003] As a processing method for improving such a point,
Add magnesium compound to wastewater containing heavy metal complex
A method of performing solid-liquid separation at H10 to H12 has been proposed (JP-A-61-192386). This method can efficiently separate heavy metals with a smaller amount of drug used as compared to the above method,
Stable processing can be performed regardless of the types of heavy metals and chelating agents. However, since the treatment is carried out in a high pH region, a large amount of an alkali agent for adjusting the pH is required, and it is necessary to neutralize again with an acid to discharge the solution, which is not always efficient.

【0004】[0004]

【発明が解決しようとする課題】本発明の課題は、低い
pH領域で処理を行うことができ、これにより少ない薬
剤使用量で効率よく重金属を分離することが可能で、処
理後の中和も不要となるほか、相乗効果も得られる重金
属錯体含有排液の処理方法を得ることである。
SUMMARY OF THE INVENTION An object of the present invention is to carry out the treatment in a low pH range, whereby it is possible to efficiently separate heavy metals with a small amount of chemicals, and to neutralize after treatment. An object of the present invention is to provide a method for treating a heavy metal complex-containing effluent that is not required and has a synergistic effect.

【0005】[0005]

【課題を解決するための手段】本発明は、重金属錯体を
含む排水に、マグネシウム化合物を重金属錯体との反応
当量以上添加し、さらに鉄および/またはアルミニウム
化合物を50〜5000mg/l添加し、pH5.5〜
9.5で固液分離することを特徴とする重金属錯体含有
排液の処理方法である。
According to the present invention, a magnesium compound is added to a wastewater containing a heavy metal complex in an amount equivalent to or more than the reaction equivalent of the heavy metal complex, and an iron and / or aluminum compound is added in an amount of 50 to 5000 mg / l and a pH of 5 .5-
9.5 A method for treating wastewater containing a heavy metal complex, comprising performing solid-liquid separation in 9.5.

【0006】本発明の処理対象とする排水は、重金属お
よびキレート剤を重金属錯体として含む排水であり、例
えばメッキ排水などがある。重金属としては、銅、クロ
ム、亜鉛、鉛、マンガン、鉄、ニッケル、カドミウムな
どがある。キレート剤としてはグルコン酸、クエン酸、
酒石酸、マロン酸などの有機酸、またはトリエタノール
アミンなどのアミン類などがある。
The wastewater to be treated in the present invention is wastewater containing a heavy metal and a chelating agent as a heavy metal complex, such as plating wastewater. Heavy metals include copper, chromium, zinc, lead, manganese, iron, nickel, cadmium and the like. Gluconic acid, citric acid,
Organic acids such as tartaric acid and malonic acid; and amines such as triethanolamine.

【0007】これらの排水に添加するマグネシウム化合
物としては、酸化マグネシウム、水酸化マグネシウム、
炭酸マグネシウム、塩化マグネシウム、硫酸マグネシウ
ムなど、マグネシウムイオンを遊離する化合物であれば
よい。これらのマグネシウム化合物は重金属錯体に対し
て反応当量以上(一般的にはMgとして20〜500m
g/l)、好ましくは反応当量の1〜3倍添加する。
Magnesium compounds added to these wastewaters include magnesium oxide, magnesium hydroxide,
Any compound that releases magnesium ions, such as magnesium carbonate, magnesium chloride, and magnesium sulfate, may be used. These magnesium compounds have a reaction equivalent of at least a heavy metal complex (generally 20 to 500 m as Mg).
g / l), preferably 1 to 3 times the reaction equivalent.

【0008】また鉄化合物としては、塩化第二鉄、硫酸
第二鉄等の第二鉄塩やポリ鉄のほか、塩化第一鉄、硫酸
第一鉄等の第一鉄塩と酸化剤の組合せなど、第二鉄イオ
ンを遊離する化合物であればよい。これらの鉄化合物は
排水に対して50〜5000mg/l、好ましくは20
0〜3000mg/l添加する。
[0008] Examples of the iron compound include ferric salts such as ferric chloride and ferric sulfate and polyiron, and a combination of a ferrous salt such as ferrous chloride and ferrous sulfate with an oxidizing agent. For example, any compound that releases ferric ion may be used. These iron compounds are contained in the wastewater in an amount of 50 to 5000 mg / l, preferably 20 to 5000 mg / l.
Add 0-3000 mg / l.

【0009】アルミニウム化合物としては、硫酸アルミ
ニウム、塩化アルミニウム、ポリ塩化アルミニウム(P
AC)等のアルミニウムイオンを遊離する化合物が使用
できる。これらのアルミニウム化合物は排水に対して5
0〜5000mg/l、好ましくは200〜3000m
g/l添加する。
As aluminum compounds, aluminum sulfate, aluminum chloride, polyaluminum chloride (P
Compounds that release aluminum ions such as AC) can be used. These aluminum compounds contribute 5 to wastewater.
0 to 5000 mg / l, preferably 200 to 3000 m
g / l.

【0010】本発明の処理方法は、重金属錯体を含む排
水に攪拌下にマグネシウム化合物を添加し、さらに鉄お
よび/またはアルミニウム化合物を添加後、pH5.5
〜9.5、好ましくは6〜9に調整し、不溶性物を固液
分離する。マグネシウム化合物を添加したのち鉄および
/またはアルミニウム化合物を添加するのが好ましい
が、場合によっては同時または逆の順序で添加してもよ
い。
In the treatment method of the present invention, a magnesium compound is added to a wastewater containing a heavy metal complex with stirring, and after adding an iron and / or aluminum compound, the pH is adjusted to 5.5.
To 9.5, preferably 6 to 9, and insoluble matter is subjected to solid-liquid separation. It is preferred to add the iron and / or aluminum compound after adding the magnesium compound, but in some cases they may be added simultaneously or in the reverse order.

【0011】これらの添加により上記pH範囲になると
きはpH調整剤を添加しなくてもよいが、上記範囲から
外れる場合はpH調整剤を添加する。pH調整剤として
は一般に水酸化ナトリウム、水酸化カルシウム等のアル
カリ剤が使用できるが、必要により塩酸、硫酸等の酸も
使用できる。
When the above-mentioned pH range is attained by these additions, it is not necessary to add a pH adjuster. In general, an alkali agent such as sodium hydroxide or calcium hydroxide can be used as the pH adjuster, but an acid such as hydrochloric acid or sulfuric acid can be used if necessary.

【0012】固液分離に際しては、ジエチルジチオカル
バミン酸塩系等の重金属捕集剤、その他の添加剤を添加
してもよく、また高分子凝集剤を添加して凝集沈殿を行
ってもよい。固液分離手段としては、沈降分離、浮上分
離、遠心分離、濾過など、通常の固液分離手段を使用で
きる。
At the time of solid-liquid separation, a heavy metal collector such as diethyldithiocarbamate and other additives may be added, or a polymer coagulant may be added to perform coagulation precipitation. As the solid-liquid separation means, ordinary solid-liquid separation means such as sedimentation separation, flotation separation, centrifugation, and filtration can be used.

【0013】攪拌混合は回転式の攪拌機による攪拌混
合、ポンプによる攪拌混合、ラインミキサによる攪拌混
合などによることができる。攪拌機の場合10〜300
rpm、好ましくは20〜150rpmとするのが好ま
しい。
The stirring and mixing can be performed by stirring and mixing using a rotary stirrer, stirring and mixing using a pump, stirring and mixing using a line mixer, and the like. 10-300 in case of stirrer
rpm, preferably 20 to 150 rpm.

【0014】上記の処理を有機酸の場合について説明す
ると、有機酸たとえばグルコン酸ナトリウムと金属イオ
ンたとえば3価のクロムが共存する場合、これらは錯体
を形成するためクロムの不溶性pH域(pH8〜9)に
しても、水酸化クロムの沈殿物は形成されず、〔1〕式
に示すように溶解状態を維持する。
The above treatment will be described in the case of an organic acid. When an organic acid such as sodium gluconate and a metal ion such as trivalent chromium coexist, they form a complex and form an insoluble pH range of chromium (pH 8 to 9). ), No precipitate of chromium hydroxide is formed, and the chromium hydroxide is maintained in a dissolved state as shown in the equation (1).

【化1】 Mg3+ + L3- → ML 〔1〕 金属イオン 有機酸 溶解状態 Embedded image Mg 3+ + L 3- → ML [1] Metal ion Organic acid dissolved state

【0015】これがアルカリ側では不安定になり、
〔2〕式のように水酸化物を生成するが、この反応は極
めて遅く排水処理にそのまま適用できない。
This becomes unstable on the alkaline side,
Although a hydroxide is generated as shown in the formula [2], this reaction is extremely slow and cannot be directly applied to wastewater treatment.

【化2】 ML + 3OH- → M(OH)3 + L3- 〔2〕## STR2 ## ML + 3OH - → M (OH ) 3 + L 3- [2]

【0016】一方、マグネシウムも有機酸と〔3〕式の
ように錯体を形成する。
On the other hand, magnesium also forms a complex with an organic acid as shown in formula [3].

【化3】 3Mg2+ + 2L3- → Mg32 〔3〕Embedded image 3Mg 2+ + 2L 3- → Mg 3 L 2 [3]

【0017】このためマグネシウムイオンの存在下にア
ルカリ性にすると、有機酸の受容体としてマグネシウム
イオンが作用し、〔4〕式のように重金属の水酸化物の
沈殿がすみやかに生じる。
For this reason, when making alkaline in the presence of magnesium ion, magnesium ion acts as an acceptor of an organic acid, and precipitation of a heavy metal hydroxide immediately occurs as shown in the formula (4).

【化4】 2ML+3Mg2++6OH- → Mg32+2M(OH)3↓ 〔4〕 マグネシウム化合物の添加量は〔4〕式における重金属
錯体との反応当量ないし3倍当量が適当であり、原水ご
とに実験的に確認することができる。
Embedded image 2ML + 3Mg 2+ + 6OH → Mg 3 L 2 + 2M (OH) 3 ↓ [4] The amount of the magnesium compound to be added is appropriately from the reaction equivalent to the heavy metal complex in the formula [4] to 3 equivalents. Can be confirmed experimentally for each case.

【0018】〔4〕式の反応では、pH10〜12の領
域において重金属の水酸化物の沈殿は急速に生じるが、
それより低いpH領域では固液分離は困難である。これ
に対して、鉄および/またはアルミニウムイオンを共存
させると、鉄および/またはアルミニウムの水酸化物と
重金属の水酸化物が共沈するため、pH5.5〜9.5
の比較的低pH領域でも固液分離が可能になる。
In the reaction of the formula [4], precipitation of heavy metal hydroxide occurs rapidly in the pH range of 10 to 12,
Solid-liquid separation is difficult in the lower pH range. On the other hand, when iron and / or aluminum ions coexist, hydroxides of iron and / or aluminum and hydroxides of heavy metals are co-precipitated, so that the pH is 5.5 to 9.5.
Solid-liquid separation becomes possible even in a relatively low pH range.

【0019】[0019]

【発明の効果】本発明によれば、重金属錯体含有排水に
マグネシウム化合物と、鉄および/またはアルミニウム
化合物と添加してpH5.5〜9.5で固液分離するこ
とにより、低いpH領域で処理を行うことができ、これ
により少ない薬剤使用量で効率よく重金属を分離するこ
とが可能で、処理後の中和も不要となるほか、それぞれ
の化合物単独で処理する場合に比べて相乗効果が得られ
る。
According to the present invention, a magnesium compound and an iron and / or aluminum compound are added to wastewater containing a heavy metal complex, and solid-liquid separation is performed at a pH of 5.5 to 9.5, thereby treating in a low pH range. This makes it possible to separate heavy metals efficiently with a small amount of drug used, eliminating the need for neutralization after treatment and achieving a synergistic effect compared to treatment with each compound alone. Can be

【0020】[0020]

【発明の実施の形態】以下、本発明の実施形態について
説明する。
Embodiments of the present invention will be described below.

【0021】実施例1〜3、比較例1〜5 クロム(III)、銅、マンガンをそれぞれ50mg/l
およびグルコン酸を100mg/l含む溶液に、攪拌下
に塩化マグネシウムを添加したのち塩化第二鉄を添加
し、その後水酸化カルシウムまたは水酸化ナトリウムで
pH調整し、15分間反応させ沈殿分離した。上澄液の
濾紙No.5A濾液分析結果を表1に示す。塩化マグネ
シウムを添加しない場合、および塩化マグネシウムだけ
を添加した場合を比較例として示す。表1の結果より、
グルコン酸錯体は鉄塩とカルシウム塩の添加だけでは処
理効果が悪いが、マグネシウム塩および鉄塩を添加し、
酸化カルシウムまたは水酸化ナトリウムでpH調整する
ことにより安定した処理効果が得られることがわかる。
Examples 1 to 3 and Comparative Examples 1 to 5 Each of chromium (III), copper and manganese was 50 mg / l.
Magnesium chloride was added to a solution containing 100 mg / l of gluconic acid and gluconic acid, and then ferric chloride was added thereto. Then, the pH was adjusted with calcium hydroxide or sodium hydroxide, and the mixture was reacted for 15 minutes to precipitate and separate. Filter paper no. Table 1 shows the results of the 5A filtrate analysis. The case where magnesium chloride is not added and the case where only magnesium chloride is added are shown as comparative examples. From the results in Table 1,
Gluconic acid complex has poor treatment effect only by adding iron salt and calcium salt, but magnesium salt and iron salt are added,
It can be seen that a stable treatment effect can be obtained by adjusting the pH with calcium oxide or sodium hydroxide.

【0022】[0022]

【表1】 [Table 1]

【0023】実施例4〜8、比較例6〜9 電子部品のメッキ排水(pH2.2、Cu92mg/
l、クエン酸100mg/l含有)を、従来ジエチルジ
チオカルバメート系重金属捕集剤と鉄塩またはアルミニ
ウム塩とを添加し、水酸化ナトリウムでpH調整して凝
集沈殿処理していたが、Cuの除去率が悪かった(比較
例)。この系に鉄塩添加前に塩化マグネシウムを添加す
ることにより、良好な除去効果が得られた。また処理p
Hは6〜9の範囲で安定した効果を示した。結果を表2
に示す。
Examples 4 to 8, Comparative Examples 6 to 9 Plating drainage of electronic parts (pH 2.2, Cu 92 mg /
l, containing 100 mg / l of citric acid), a conventional diethyldithiocarbamate-based heavy metal scavenger and an iron salt or an aluminum salt were added thereto, and the pH was adjusted with sodium hydroxide for coagulation precipitation treatment. The rate was poor (Comparative Example). By adding magnesium chloride to the system before adding the iron salt, a good removal effect was obtained. Also processing p
H showed a stable effect in the range of 6 to 9. Table 2 shows the results
Shown in

【0024】[0024]

【表2】 [Table 2]

【0025】上記の結果より、マグネシウム化合物と鉄
またはアルミニウム化合物とを併用する実施例のものは
いずれも低いpH領域で優れた処理水質が得られてお
り、それぞれの化合物単独で処理する比較例に比べて相
乗効果が得られていることがわかる。
From the above results, all of the examples in which a magnesium compound and an iron or aluminum compound are used together have excellent treated water quality in a low pH range. This shows that a synergistic effect is obtained.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 重金属錯体を含む排水に、マグネシウム
化合物を重金属錯体との反応当量以上添加し、さらに鉄
および/またはアルミニウム化合物を50〜5000m
g/l添加し、pH5.5〜9.5で固液分離すること
を特徴とする重金属錯体含有排液の処理方法。
1. A magnesium compound is added to a wastewater containing a heavy metal complex in an amount of at least a reaction equivalent of the heavy metal complex, and an iron and / or aluminum compound is added in an amount of 50 to 5000 m.
g / l, and solid-liquid separation at pH 5.5 to 9.5.
JP00442499A 1999-01-11 1999-01-11 Treatment method of waste liquid containing heavy metal complex Expired - Fee Related JP4374636B2 (en)

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JP2019069434A (en) * 2017-10-06 2019-05-09 東ソー株式会社 Purification agent for nickel-containing aqueous solution and purification method of nickel-containing aqueous solution
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