JPH0564240B2 - - Google Patents
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- Publication number
- JPH0564240B2 JPH0564240B2 JP59223846A JP22384684A JPH0564240B2 JP H0564240 B2 JPH0564240 B2 JP H0564240B2 JP 59223846 A JP59223846 A JP 59223846A JP 22384684 A JP22384684 A JP 22384684A JP H0564240 B2 JPH0564240 B2 JP H0564240B2
- Authority
- JP
- Japan
- Prior art keywords
- zinc
- waste liquid
- plating
- carbonate
- electrogalvanizing
- 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.)
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Description
【発明の詳細な説明】
(産業上の利用分野)
本発明は、硫酸亜鉛を主成分とするような酸性
電気亜鉛めつき廃液から亜鉛分を回収し、めつき
浴に再利用する方法に関する。DETAILED DESCRIPTION OF THE INVENTION (Industrial Application Field) The present invention relates to a method for recovering zinc from an acidic electrolytic galvanizing waste solution containing zinc sulfate as a main component and reusing it in a plating bath.
(従来の技術)
電気亜鉛めつき鋼板は、溶融亜鉛めつき鋼板に
比べて、加工性がよく、めつき量が少なく、表面
が平滑であることから、加工性や表面外観を要求
される屋内用途に主として利用され、このめつき
は硫酸亜鉛を主成分とする酸性浴が主に用いられ
ている。(Conventional technology) Compared to hot-dip galvanized steel sheets, electrogalvanized steel sheets have better workability, less plating, and a smoother surface, so they can be used indoors where workability and surface appearance are required. It is mainly used for this purpose, and an acidic bath containing zinc sulfate as a main component is mainly used for this plating.
一般に、電気めつきを行う場合、浴組成を一定
に保つためにめつき液の補給に伴うめつき液の汲
み出し、或いは場合により老化めつき液の入れ替
えが必要となり、有害な重金属を含有するめつき
廃液が生ずる。あるいは水バランス維持のため廃
液が生じる。環境保全のために、かかるめつき廃
液を中和および無害化処理してから廃棄しなけれ
ばならないことは周知である。 Generally, when performing electroplating, in order to maintain a constant bath composition, it is necessary to pump out the plating solution when replenishing the plating solution, or in some cases, to replace aging plating solution, which may cause plating that contains harmful heavy metals. Waste liquid is produced. Alternatively, waste liquid is generated to maintain water balance. It is well known that in order to protect the environment, such plating waste liquid must be neutralized and rendered harmless before being disposed of.
硫酸亜鉛を主体とするような酸性電気亜鉛めつ
き浴からの廃液の処理は、従来、Ca(OH)2等を
利用した単なる中和処理により行われている。こ
れにより、亜鉛は水酸化亜鉛として沈澱するが、
分離したスラツジは廃棄され、廃棄物の利用はな
されていないのが現状である。 Conventionally, waste liquid from acidic electrogalvanizing baths containing zinc sulfate as a main ingredient has been treated by simple neutralization using Ca(OH) 2 or the like. As a result, zinc precipitates as zinc hydroxide,
At present, the separated sludge is discarded and the waste is not used.
一方、副生亜鉛ダストまたはアツシユなどの亜
鉛含有副生物からの亜鉛の回収方法として、硫酸
亜鉛溶液にソーダ灰(Na2CO3、すなわち炭酸ナ
トリウム)を添加して、塩基性炭酸亜鉛を析出さ
せ、分離回収することは公知であるが、電気亜鉛
めつき廃液についての亜鉛分の回収法に関する提
案は従来ほとんどなかつた。 On the other hand, as a method for recovering zinc from zinc-containing by-products such as by-product zinc dust or ash, basic zinc carbonate is precipitated by adding soda ash (Na 2 CO 3 , i.e., sodium carbonate) to a zinc sulfate solution. Although it is known that the zinc content can be separated and recovered, there have been few proposals regarding a method for recovering the zinc content from electrogalvanizing waste liquid.
また、特開昭59−88319号には、Fe,Pbが共存
する亜鉛塩溶液から炭酸アンモニウムにより炭酸
亜鉛を析出させるにあたつて、予じめ金属亜鉛を
添加して溶存重金属イオンを析出させ分別するこ
とが記載されている。 Furthermore, in JP-A-59-88319, when precipitating zinc carbonate with ammonium carbonate from a zinc salt solution in which Fe and Pb coexist, metal zinc is added in advance to precipitate dissolved heavy metal ions. It is stated that it should be separated.
(発明が解決しようとする問題点)
現状では無害化処理後、廃棄されている電気亜
鉛めつき廃液中に高濃度で含有されているZn分
の回収とめつき浴への再利用が可能となれば、こ
れは廃液中のZn分の有効活用のほかに、亜鉛源
の使用原単位の低減にもつながり、有利である。
また、めつき廃液の処理コストの低減が望ましい
ことは云うまでもない。(Problem to be solved by the invention) It would be possible to recover Zn, which is presently contained in a high concentration in electrogalvanizing waste liquid that is discarded after detoxification treatment, and reuse it in a plating bath. For example, this is advantageous because it not only makes effective use of the Zn content in the waste liquid, but also leads to a reduction in the unit consumption of the zinc source.
It goes without saying that it is desirable to reduce the cost of treating plating waste liquid.
(問題点を解決するための手段)
そこで、本発明者らは、鋼板などの電気亜鉛め
つきに多用されている酸性電気亜鉛めつき浴の廃
液について、これから亜鉛を回収できる経済的な
廃液処理法を開発すべく研究を重ねた結果、めつ
き液は精製された原料を使用しているため、めつ
き廃液も比較的溶存不純物が少ないことに着目し
て、亜鉛を塩基性炭酸亜鉛として析出させるよう
に炭酸アルカリと水酸化アルカリで中和処理する
と、析出した塩基性炭酸亜鉛は酸性電気亜鉛めつ
きの亜鉛源として再利用でき、こうしてもめつき
の操業に悪影響がないことを見い出し、本発明を
完成した。(Means for Solving the Problems) Therefore, the present inventors have developed an economical waste liquid treatment method that can recover zinc from the waste liquid of acidic electrogalvanizing baths that are often used for electrogalvanizing steel plates, etc. As a result of repeated research to develop the method, we focused on the fact that since the plating solution uses purified raw materials, the plating waste solution also has relatively few dissolved impurities, and we decided to precipitate zinc as basic zinc carbonate. They discovered that by neutralizing with alkali carbonate and alkali hydroxide, the precipitated basic zinc carbonate can be reused as a zinc source for acid electrogalvanizing, and that this does not have any negative effects on plating operations, and has completed the present invention. did.
ここに、本発明は、酸性浴電気亜鉛めつき廃液
に、予め酸化剤を添加した後に粉末亜鉛を添加し
て、亜鉛よりイオン化傾向の低い溶存重金属不純
物を析出させ除去してから、酸性浴電気亜鉛めつ
き廃液を、炭酸ナトリウムまたは炭酸ナトリウム
と水酸化ナトリウムにより中和して塩基性炭酸亜
鉛を析出させ、析出結晶を水洗して水溶性不純物
を除去した後、得られた塩基性炭酸亜鉛をスラリ
ー状のまま或いは分離乾燥により得た固体粉末状
で酸性亜鉛電気めつき浴に供給して亜鉛源として
再利用することを特徴とする、電気亜鉛めつき廃
液からの亜鉛の回収および利用方法である。 Here, the present invention adds powdered zinc after adding an oxidizing agent to acidic bath electrogalvanizing waste liquid to precipitate and remove dissolved heavy metal impurities that have a lower ionization tendency than zinc, and then The zinc plating waste liquid is neutralized with sodium carbonate or sodium carbonate and sodium hydroxide to precipitate basic zinc carbonate, and the precipitated crystals are washed with water to remove water-soluble impurities. A method for recovering and utilizing zinc from electrogalvanizing waste liquid, which is characterized in that it is supplied as a slurry or as a solid powder obtained by separation and drying to an acidic zinc electroplating bath and reused as a zinc source. be.
(作用)
本発明で処理の対象とするのは酸性浴、特に硫
酸亜鉛を主成分とする電気亜鉛めつき液の廃液
(以下、単にめつき廃液とも云う)である。この
ようなめつき液は、一般に硫酸亜鉛のほかに、ア
ンモニウム、ナトリウム、マグネシウム、アルミ
ニウムなどの硫酸塩を少量含有し、PHは1〜4.5
の範囲内である。このめつき液の廃液には、被め
つき基体から溶出してきたFe分のほかに、微量
のPb,Cdなどの重金属イオンが一般に溶存して
いる。しかし、上述のようにめつき液は一般に精
製された原料を使用しており、そのためめつき廃
液中の不純物量もかなり低い。したがつて、酸性
浴電気亜鉛めつき廃液を本発明にしたがつてその
まま中和処理に付すことができる。(Function) The object of the present invention is an acid bath, particularly waste liquid of an electrolytic galvanizing solution containing zinc sulfate as a main component (hereinafter also simply referred to as plating waste liquid). In addition to zinc sulfate, such plating solutions generally contain small amounts of sulfates such as ammonium, sodium, magnesium, and aluminum, and have a pH of 1 to 4.5.
is within the range of In addition to the Fe components eluted from the plated substrate, trace amounts of heavy metal ions such as Pb and Cd are generally dissolved in the waste plating solution. However, as mentioned above, the plating solution generally uses purified raw materials, and therefore the amount of impurities in the plating waste solution is quite low. Therefore, acid bath electrogalvanizing waste liquid can be directly subjected to neutralization treatment according to the present invention.
ただし、めつき廃液がPb,Fe等の重金属不純
物の溶存イオンを多く含む場合、またはこのよう
な不純物を極力除去したい場合に対応するため、
かかる不純物を除去する適当な処理を中和前に予
め施しておく。このため方法は、めつき廃液にま
ず酸化剤を添加し、次いで亜鉛粉末を添加して亜
鉛よりイオン化傾向の低い重金属イオンをイオン
化傾向の差を利用して金属として沈澱させ、除去
する方法である。これは、次に示すように、亜鉛
のイオン化傾向が高いことを利用したものであ
る。 However, in cases where the plating waste liquid contains many dissolved ions of heavy metal impurities such as Pb and Fe, or when it is desired to remove such impurities as much as possible,
Appropriate treatment to remove such impurities is performed before neutralization. For this reason, the method is to first add an oxidizing agent to the plating waste liquid, then add zinc powder, and use the difference in ionization tendency to precipitate and remove heavy metal ions, which have a lower ionization tendency than zinc, as metals. . This takes advantage of the high ionization tendency of zinc, as shown below.
K>Ca>Na>Mg>Al>Zn>Cr>Fe2+>Cd>
Co>Ni>Sn>Pb>Fe3+
酸化剤を先に添加するのは、Fe2+イオンをイ
オン化傾向のずつと低いFe3+に酸化して、Feの
沈殿を確実にするためである。この酸化剤として
はH2O2が好ましい。他の酸化剤、たとえば
HNO3,KMnO4,HCrO4等でも上記の目的は達
せられるが、処理すべき廃液に新たな不純物を導
入することになる。亜鉛粉末はZnをイオン化さ
せて、溶存重金属イオンを金属として沈殿させる
というイオン交換反応を促進するため細かい程よ
く、通常88μ以下の微粉末を用いるのが好まし
い。これにより沈殿した不純物は、濾過等の分離
手段により除去する。K>Ca>Na>Mg>Al>Zn>Cr>Fe 2+ >Cd>
Co>Ni>Sn>Pb>Fe 3+ The reason for adding the oxidizing agent first is to oxidize Fe 2+ ions to Fe 3+ with a lower ionization tendency and ensure the precipitation of Fe. . H 2 O 2 is preferred as this oxidizing agent. Other oxidizing agents, e.g.
Although HNO 3 , KMnO 4 , HCrO 4 , etc. can also achieve the above purpose, they introduce new impurities into the waste liquid to be treated. The finer the zinc powder, the better, in order to promote the ion exchange reaction in which Zn is ionized and dissolved heavy metal ions are precipitated as metal, and it is usually preferable to use a fine powder of 88 μm or less. Impurities precipitated by this are removed by separation means such as filtration.
上述のように不純物を除去しためつき廃液、
に、本発明により炭酸ナトリウムまたはこれと水
酸化ナトリウムとを添加して、めつき廃液を中和
すると同時に亜鉛分を塩基性炭酸亜鉛として析出
させる。めつき廃液中の亜鉛分が硫酸亜鉛である
場合の反応式を次に示す。 The waste liquid from which impurities have been removed as described above,
According to the present invention, sodium carbonate or sodium carbonate and sodium hydroxide are added to neutralize the plating waste liquid and simultaneously precipitate the zinc component as basic zinc carbonate. The reaction formula when the zinc content in the plating waste liquid is zinc sulfate is shown below.
5ZnSO4+6NaOH+2Na2CO3→〔Zn(OH)2〕3
〔ZnCO3〕2↓+5Na2SO4
塩基性炭酸亜鉛は組成が一定でないが、代表的
なものは上記組成のものである。この塩を生成さ
せるには、上式からわかるようにNaOH:Na2
CO3のモル比は3:1とすべきである。しかし、
Na2CO3は水に溶解すると、次式にしたがつて
NaOHを生成する。5ZnSO 4 +6NaOH+2Na 2 CO 3 → [Zn(OH) 2 ] 3
[ZnCO 3 ] 2 ↓+5Na 2 SO 4Although the composition of basic zinc carbonate is not constant, the typical one has the above composition. To generate this salt, NaOH:Na 2
The molar ratio of CO 3 should be 3:1. but,
When Na 2 CO 3 is dissolved in water, it becomes
Generates NaOH.
Na2CO3+H2O→NaOH+NaHCO3
そのため、NaOHの添加量は上記のモル比の
割合より少なくてよく、さらにはNaOHを加え
ずにNa2CO3のみを加えても、塩基性炭酸亜鉛が
生成して析出する。また、遊離の強酸の含有量が
高く、そのため強酸性を示すめつき廃液の場合に
は、NaOHを上記モル比より多く添加してもよ
い。このように、NaOHを加える場合でも、
NaOHとNa2CO3の割合は状況、特に廃液の酸性
度に応じて広範囲に変動させうる。中和処理によ
りめつき廃液のPHを約7.0〜7.5にするのが好まし
い。Na 2 CO 3 + H 2 O → NaOH + NaHCO 3 Therefore, the amount of NaOH added may be less than the above molar ratio, and even if only Na 2 CO 3 is added without adding NaOH, basic zinc carbonate It forms and precipitates. In addition, in the case of a plating waste liquid that has a high content of free strong acid and therefore exhibits strong acidity, NaOH may be added in an amount greater than the above molar ratio. In this way, even when adding NaOH,
The proportion of NaOH and Na 2 CO 3 can be varied within a wide range depending on the circumstances, especially the acidity of the effluent. It is preferable to adjust the pH of the plating waste liquid to about 7.0 to 7.5 by neutralization treatment.
次いで、析出した塩基性炭酸亜鉛を水で洗浄し
た後、水性スラリー状態または固体状態で回収
し、めつき浴に再循環させる。 The precipitated basic zinc carbonate is then washed with water and then recovered in an aqueous slurry or solid state and recycled to the plating bath.
洗浄回収工程は常法で実施できる。たとえば、
析出物を濾過により分離するか、或いは分離せず
にそのままリパルプ洗浄(すなわち、多量の水中
に分散させて濾過することにより水溶性不純物を
除去する操作)を必要により1回あるいは数回く
り返し、塩基性炭酸亜鉛のスラリーを得る。こう
して得られたスラリー状の塩基性炭酸亜鉛を、例
えば分離シツクナー等で濃縮して、そのまま電気
亜鉛めつき浴に再循環させて亜鉛源として再利用
する。あるいは、スラリーを濾過し、得られたケ
ーキを乾燥して粉末状の塩基性炭酸亜鉛成品を
得、これをめつき浴に再循環させてもよい。もち
ろん、こうして回収した粉末成品は他の用途に亜
鉛供給源として使用することもできる。 The washing and recovery step can be carried out in a conventional manner. for example,
Separate the precipitate by filtration, or repeat repulping washing (i.e., removing water-soluble impurities by dispersing it in a large amount of water and filtration) once or several times as necessary. Obtain a slurry of zinc carbonate. The slurry-like basic zinc carbonate thus obtained is concentrated using, for example, a separation thickener, and is recycled as it is to the electrogalvanizing bath to be reused as a zinc source. Alternatively, the slurry may be filtered and the resulting cake dried to provide a powdered basic zinc carbonate product that is recycled to the plating bath. Of course, the powder product thus recovered can also be used as a zinc source for other applications.
塩基性炭酸亜鉛は水には不溶性であるが、酸に
は可溶である。すなわち、酸性めつき浴にZn源
としてこれを添加すると、めつき液中に存在する
遊離の酸、たとえば硫酸と反応して可溶性の亜鉛
塩(例、硫酸亜鉛)を生成し、めつき浴に溶解す
る。したがつて、塩基性炭酸亜鉛は酸性めつき浴
にZn源として供給するのに適した化合物である。
また、めつき廃液から回収される程度の量の塩基
性炭酸亜鉛を通常の硫酸亜鉛を主成分とするめつ
き液にZn源として補給しても、めつき効率の低
下その他の操業への悪影響はまつたくなく、Zn
源として有効に活用されることがわかつた。 Basic zinc carbonate is insoluble in water but soluble in acid. That is, when it is added as a Zn source to an acidic plating bath, it reacts with the free acid present in the plating solution, such as sulfuric acid, to produce a soluble zinc salt (e.g., zinc sulfate), which is added to the plating bath. dissolve. Basic zinc carbonate is therefore a suitable compound to supply as a Zn source to acidic plating baths.
Furthermore, even if basic zinc carbonate, recovered from plating waste liquid, is added as a Zn source to a plating liquid mainly composed of zinc sulfate, there will be no reduction in plating efficiency or other negative effects on operations. Without eyelashes, Zn
It was found that it can be effectively used as a source.
電気めつき廃液中には未反応の遊離酸、例えば
硫酸が含まれているのが普通である。この遊離酸
を利用して、廃液中に金属亜鉛含有源、たとえば
亜鉛含有ダストを添加し、亜鉛と酸との反応によ
り亜鉛を溶解させて、廃液中の亜鉛濃度を高めて
から本発明方法を実施してもよい。そのために
は、廃液中の遊離酸の濃度が少なくとも
0.25mol/以上であることが好ましい。亜鉛含
有ダストは、例えば製鉄所の溶融めつきラインお
よびダスト還元鉄設備等で発生し、その組成は、
例えば、Zn:44.5%、Fe:15.7%、Pb:6.1%、
C:3.8%、Cl:3.0%、SiO2:2.0%およびCa:
1.9%である。このような亜鉛含有ダストをめつ
き廃液に添加してZn濃度の富化を図る場合、上
記の組成の例からもわかるように、亜鉛と共に他
の不純物も混入することになるので、本発明によ
る中和処理を行う前に、上述したイオン交換反応
を利用した不純物除去処理を実施するのが好まし
い。 Electroplating waste liquid usually contains unreacted free acids, such as sulfuric acid. Utilizing this free acid, a metallic zinc-containing source, such as zinc-containing dust, is added to the waste liquid, and the zinc is dissolved by the reaction between zinc and the acid, increasing the zinc concentration in the waste liquid, and then the method of the present invention is carried out. May be implemented. For this purpose, the concentration of free acid in the waste liquid must be at least
It is preferably 0.25 mol/or more. Zinc-containing dust is generated, for example, in hot-dip galvanizing lines and dust-reduced iron equipment in steel plants, and its composition is as follows:
For example, Zn: 44.5%, Fe: 15.7%, Pb: 6.1%,
C: 3.8%, Cl: 3.0%, SiO2 : 2.0% and Ca:
It is 1.9%. When such zinc-containing dust is added to the plating waste liquid to enrich the Zn concentration, as can be seen from the above composition example, other impurities will be mixed in with zinc. Before performing the neutralization treatment, it is preferable to perform an impurity removal treatment using the above-mentioned ion exchange reaction.
次に、本発明を実施例により具体的に説明す
る。 Next, the present invention will be specifically explained using examples.
実施例
硫酸亜鉛を主成分とする鋼板の電気亜鉛めつき
浴から排出されためつき廃液(Zn含有量:金属
Znとして73.1g/)500c.c.に、30%H2O2水溶液
30c.c.を加え、常温で30分間攪拌した。次に50gの
亜鉛粉を加え、常温でさらに30分間攪拌した。こ
の溶液を吸引濾過して未溶解の亜鉛粉と沈殿した
不純物とを分離した。Example: A waste solution discharged from an electrolytic galvanizing bath for steel sheets containing zinc sulfate as the main component (Zn content: metal
73.1g/) 500c.c. as Zn, 30% H 2 O 2 aqueous solution
30 c.c. was added and stirred at room temperature for 30 minutes. Next, 50 g of zinc powder was added and stirred for an additional 30 minutes at room temperature. This solution was suction filtered to separate undissolved zinc powder and precipitated impurities.
この濾液500c.c.に、濾液の中和処理に必要な
30.5gのNaOHおよび27.0gのNa2CO3を含む500
c.c.のアルカリ水溶液を加え、常温で30分間攪拌し
て塩基性炭酸亜鉛の結晶を析出させた。この反応
液を吸引濾過し、回収したケーキにはさらに1
の純水によるリパルプ洗浄を3回行つて水溶性不
純物を除去した。リパルプ洗浄は1回毎に1の
純水を加えて常温で30分間攪拌し、濾過すること
により行つた。最後に105℃で乾燥して、69.3g
の固体粉末を得た。この粉末の分析結果は次の通
りであつた。 This 500 c.c. of filtrate contains the necessary amount for neutralizing the filtrate.
500 containing 30.5g NaOH and 27.0g Na2CO3
cc of alkaline aqueous solution was added and stirred at room temperature for 30 minutes to precipitate basic zinc carbonate crystals. This reaction solution was suction-filtered, and the recovered cake was further added with 1
Repulp washing with pure water was performed three times to remove water-soluble impurities. Repulp washing was carried out by adding 1 part of pure water each time, stirring at room temperature for 30 minutes, and filtering. Finally dried at 105℃, 69.3g
A solid powder was obtained. The analysis results of this powder were as follows.
Zn:58.52% Fe:4.5ppm
Pb:0.8ppm Cd:0.1ppm
Cl:10.3ppm
この粉末はめつき操業に悪影響を及ばさずに酸
性電気亜鉛めつきに十分使用できる。 Zn: 58.52% Fe: 4.5ppm Pb: 0.8ppm Cd: 0.1ppm Cl: 10.3ppm This powder can be used satisfactorily for acid electrogalvanizing without adversely affecting plating operations.
(発明の効果)
以上の説明より明らかなように、本発明によれ
ば酸性浴電気亜鉛めつき廃液からこれに含まれる
亜鉛分を回収してめつきに有効に再利用すること
ができ、めつきに必要な亜鉛源使用原単位を低減
させることができると共に、中和により生ずる廃
棄物量が減少するので、廃棄物処理コストの低減
にもつながる。また、中和に使用する炭酸ナトリ
ウム(ソーダ灰)および水酸化ナトリウムはいず
れも製鉄所内で副生物として得ることもできる比
較的安価な物質であるので、本発明の方法は経済
的に実施でき、廃液処理コストの低減にもなる。
また、実施例に示すように亜鉛分は高純度で回収
されるので、本発明によりこれを電気亜鉛めつき
浴に再循環させても、めつき操業に支障は出な
い。(Effects of the Invention) As is clear from the above explanation, according to the present invention, the zinc contained in the acid bath electrogalvanizing waste liquid can be recovered and effectively reused for plating. In addition to reducing the unit consumption of zinc sources required for neutralization, the amount of waste generated by neutralization is also reduced, leading to a reduction in waste treatment costs. In addition, the method of the present invention can be carried out economically, since the sodium carbonate (soda ash) and sodium hydroxide used for neutralization are both relatively inexpensive substances that can be obtained as by-products within steel mills. It also reduces waste liquid treatment costs.
Further, as shown in the examples, since the zinc content is recovered in high purity, even if it is recycled to the electrogalvanizing bath according to the present invention, there will be no problem in the plating operation.
Claims (1)
次いで亜鉛粉末を添加して、亜鉛よりイオン化傾
向の低い溶存重金属不純物を析出させ、除去して
から、該酸性浴電気亜鉛めつき廃液を、炭酸ナト
リウムまたは炭酸ナトリウムと水酸化ナトリウム
により中和して塩基性炭酸亜鉛を析出させ、析出
結晶を水洗して水溶性不純物を除去した後、得ら
れた塩基性炭酸亜鉛をスラリー状のまま或いは分
離乾燥により得た固体粉末状で酸性亜鉛電気めつ
き浴に供給して亜鉛源として再利用することを特
徴とする、電気亜鉛めつき廃液からの亜鉛の回収
および利用方法。 2 酸化剤と亜鉛粉末の添加前に、酸性浴電気亜
鉛めつき廃液に亜鉛含有ダストを加えて、廃液の
亜鉛濃度を高めることをさらに特徴とする特許請
求の範囲第1項記載の方法。[Claims] 1. An oxidizing agent,
Zinc powder is then added to precipitate and remove dissolved heavy metal impurities that have a lower ionization tendency than zinc, and the acid bath electrogalvanizing waste liquid is then neutralized with sodium carbonate or sodium carbonate and sodium hydroxide. After precipitating basic zinc carbonate and washing the precipitated crystals with water to remove water-soluble impurities, the obtained basic zinc carbonate is applied as a slurry or as a solid powder obtained by separation and drying to an acidic zinc electroplating bath. A method for recovering and utilizing zinc from electrolytic galvanizing waste solution, characterized by supplying the zinc to a zinc source and reusing it as a zinc source. 2. The method of claim 1 further comprising adding zinc-containing dust to the acid bath electrogalvanizing effluent to increase the zinc concentration of the effluent before adding the oxidizing agent and zinc powder.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP22384684A JPS61104100A (en) | 1984-10-26 | 1984-10-26 | Method for recovering and utilizing zinc from waste zinc electroplating liquid |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP22384684A JPS61104100A (en) | 1984-10-26 | 1984-10-26 | Method for recovering and utilizing zinc from waste zinc electroplating liquid |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS61104100A JPS61104100A (en) | 1986-05-22 |
| JPH0564240B2 true JPH0564240B2 (en) | 1993-09-14 |
Family
ID=16804637
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP22384684A Granted JPS61104100A (en) | 1984-10-26 | 1984-10-26 | Method for recovering and utilizing zinc from waste zinc electroplating liquid |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS61104100A (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS63186897A (en) * | 1987-01-29 | 1988-08-02 | Tsukishima Kikai Co Ltd | Method for purifying plating liquid |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3953306A (en) * | 1973-10-03 | 1976-04-27 | Dart Environment And Services Company | Metal recovery from waste treatment sludges |
-
1984
- 1984-10-26 JP JP22384684A patent/JPS61104100A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS61104100A (en) | 1986-05-22 |
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