JPH04325414A - Production of zinc oxide-zinc hydroxide mixture - Google Patents

Production of zinc oxide-zinc hydroxide mixture

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Publication number
JPH04325414A
JPH04325414A JP9536991A JP9536991A JPH04325414A JP H04325414 A JPH04325414 A JP H04325414A JP 9536991 A JP9536991 A JP 9536991A JP 9536991 A JP9536991 A JP 9536991A JP H04325414 A JPH04325414 A JP H04325414A
Authority
JP
Japan
Prior art keywords
zinc
reaction
mixture
zinc oxide
acidic wastewater
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
JP9536991A
Other languages
Japanese (ja)
Other versions
JP3185240B2 (en
Inventor
Masatoshi Kamigaki
上垣 正俊
Tomitaka Nakajima
富隆 中島
Takanori Ito
孝徳 伊藤
Takenori Mori
武則 森
Shigeki Nakada
仲田 茂樹
Yasuo Noami
野網 靖雄
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.)
Sumitomo Chemical Co Ltd
Original Assignee
Sumitomo Chemical Co Ltd
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Priority to JP09536991A priority Critical patent/JP3185240B2/en
Publication of JPH04325414A publication Critical patent/JPH04325414A/en
Application granted granted Critical
Publication of JP3185240B2 publication Critical patent/JP3185240B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Abstract

PURPOSE:To obtain a high-quality zinc oxide-zinc hydroxide mixture having high separability from water. CONSTITUTION:Acidic waste water contg. zinc salts is added to an aq. soln. of sodium hydroxide or potassium hydroxide to produce a zinc oxide-zinc hydroxide mixture by a batch system. At the end of reaction, pH is about 9.5-12.5.

Description

【発明の詳細な説明】[Detailed description of the invention]

【0001】0001

【産業上の利用分野】本発明は苛性ソーダ又は苛性カリ
水溶液中に亜鉛塩を含む酸性廃水を添加して酸化亜鉛及
び水酸化亜鉛混合物を製造するバッチ式方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a batch process for producing a zinc oxide and zinc hydroxide mixture by adding acidic wastewater containing zinc salts to an aqueous solution of caustic soda or potassium hydroxide.

【0002】0002

【従来の技術】特開昭57−149827号公報には無
機亜鉛水溶液とアルカリ水溶液とを撹拌反応槽中へ同時
に連続して添加しながら撹拌反応する同時添加反応を、
その反応スラリーpH値を下限pH値=8−0.033
4tから上限pH値=12.7−0.0578t(ただ
しtは反応温度〔℃〕を示す)の範囲内に保ちながら、
また得られる同時添加反応生成スラリー中の全Zn濃度
が20g/L以上となるように行い、場合によっては生
じた同時添加反応終了スラリーにアルカリまたは無機亜
鉛塩を追加添加し、且つ、全無機亜鉛塩使用量に対して
全アルカリ使用量が0.95当量以上の割合(即ち全無
機亜鉛塩使用量のZn原子1個に対して全アルカリ使用
量のOH基1.9個以上の割合)となるようにして沈澱
物を得ることを特徴とする亜鉛酸化物の製造方法が記載
されている。また、特開昭53−61593号公報には
塩基性塩類を含まない水酸化亜鉛の製造方法として、苛
性ソーダ等のアルカリ溶液に亜鉛を含有する酸性溶液を
添加する方法が記載されている。さらに、特開昭60−
171222号公報には、亜鉛酸塩を含むpH12.5
以上のアルカリ性溶液に、酸を加えてpH12.5〜p
H8まで中和することにより直接酸化亜鉛を生成させる
ことを特徴とする湿式法による酸化亜鉛の製造方法が記
載されている。
[Prior Art] JP-A-57-149827 discloses a simultaneous addition reaction in which an inorganic zinc aqueous solution and an alkaline aqueous solution are simultaneously and continuously added to a stirring reaction tank and reacted with stirring.
Lower limit pH value of the reaction slurry = 8-0.033
While keeping within the range from 4t to upper limit pH value = 12.7-0.0578t (where t indicates the reaction temperature [°C]),
In addition, the total Zn concentration in the resulting slurry produced by the simultaneous addition reaction is 20 g/L or more, and in some cases, an alkali or inorganic zinc salt is additionally added to the slurry produced after the simultaneous addition reaction, and all inorganic zinc is The ratio of the total amount of alkali used to the amount of salt used is 0.95 equivalent or more (i.e. the ratio of 1.9 or more OH groups of the total amount of alkali used to one Zn atom of the total amount of inorganic zinc salt used) A method for producing zinc oxide is described, which is characterized in that a precipitate is obtained as follows. Further, Japanese Patent Application Laid-Open No. 53-61593 describes a method for producing zinc hydroxide free of basic salts, in which an acidic solution containing zinc is added to an alkaline solution such as caustic soda. Furthermore, JP-A-60-
No. 171222 discloses that pH 12.5 containing zincate
Add acid to the above alkaline solution to pH 12.5~p
A method for producing zinc oxide by a wet method is described, which is characterized in that zinc oxide is directly produced by neutralizing to H8.

【0003】0003

【発明が解決しようとする課題】亜鉛塩を含む酸性廃水
をアルカリで処理して酸化亜鉛及び水酸化亜鉛混合物を
製造する場合は、反応混合物中の酸化亜鉛及び水酸化亜
鉛混合物と水との分離性、例えば濾過性が悪く、従って
分離後の含水率の高いケーキを乾燥する際に長時間を要
することになり、著しく生産性が損なわれている。本発
明者らは分離性の良好な、従って生産性の良い酸化亜鉛
及び水酸化亜鉛混合物の製造方法を鋭意検討の結果、本
発明を完成した。
[Problem to be Solved by the Invention] When a zinc oxide and zinc hydroxide mixture is produced by treating acidic wastewater containing zinc salts with an alkali, it is necessary to separate the zinc oxide and zinc hydroxide mixture from water in the reaction mixture. For example, the filterability is poor, and therefore, it takes a long time to dry a cake with a high water content after separation, which significantly impairs productivity. The present inventors have completed the present invention as a result of intensive studies on a method for producing a zinc oxide and zinc hydroxide mixture with good separability and therefore good productivity.

【0004】0004

【課題を解決するための手段】本発明は、苛性ソーダ又
は苛性カリ水溶液中に亜鉛塩を含む酸性廃水を添加して
酸化亜鉛及び水酸化亜鉛混合物を製造するバッチ式方法
であって、且つ反応終了時のpHが約9.5〜約12.
5の範囲であることを特徴とする方法である。亜鉛塩を
含む酸性廃水としては、例えば塩化亜鉛、酢酸亜鉛、硫
酸亜鉛、硝酸亜鉛等の亜鉛塩またはこれらの混合物を含
む工場廃水等が挙げられる。好ましくは、亜鉛塩として
塩化亜鉛及び/又は酢酸亜鉛を、酸性廃水中、約10〜
約30重量%含むものが挙げられる。酸性廃水の添加時
間については、長時間であるときに生成する酸化亜鉛及
び水酸化亜鉛混合物の粒子径が大きくなり、分離性、例
えば濾過性も良好である。しかしながら、生産性の観点
からは通常約30分〜約20時間であり、好ましくは約
1時間〜約10時間である。反応温度については、高温
、例えば60℃以上では生成した酸化亜鉛及び水酸化亜
鉛混合物の中、微粒子分が増加するので好ましくなく、
0〜40℃であることが好ましい。特に好ましくは10
〜30℃である。反応混合物中の亜鉛塩濃度はZnとし
て通常約30〜約120g/Lであり、好ましくは約6
0〜約110g/Lである。反応終了後、反応混合物で
ある酸化亜鉛及び水酸化亜鉛混合物のけんだく液から、
該混合物を適当な分離手段、例えば沈降分離、加圧濾過
、減圧濾過、セントル濾過、デカンター等により水と分
離後、得られたウエットケーキを公知の手段で乾燥する
ことにより酸化亜鉛及び水酸化亜鉛混合物が得られる。
[Means for Solving the Problems] The present invention is a batch method for producing a zinc oxide and zinc hydroxide mixture by adding acidic wastewater containing zinc salts to a caustic soda or caustic potassium aqueous solution, and pH of about 9.5 to about 12.
This method is characterized by a range of 5. Examples of acidic wastewater containing zinc salts include factory wastewater containing zinc salts such as zinc chloride, zinc acetate, zinc sulfate, and zinc nitrate, or mixtures thereof. Preferably, zinc chloride and/or zinc acetate as zinc salts are added in acidic wastewater at a concentration of about 10 to
Examples include those containing about 30% by weight. As for the addition time of acidic wastewater, if the addition time is long, the particle size of the zinc oxide and zinc hydroxide mixture that is produced becomes large, and the separability, for example, the filterability is also good. However, from the viewpoint of productivity, the time is usually about 30 minutes to about 20 hours, preferably about 1 hour to about 10 hours. Regarding the reaction temperature, a high temperature, for example 60°C or higher, is not preferable because it increases the amount of fine particles in the produced zinc oxide and zinc hydroxide mixture.
The temperature is preferably 0 to 40°C. Particularly preferably 10
~30°C. The concentration of zinc salt in the reaction mixture is usually about 30 to about 120 g/L as Zn, preferably about 6
0 to about 110 g/L. After the reaction is completed, from the suspension of the reaction mixture of zinc oxide and zinc hydroxide,
After separating the mixture from water by a suitable separation means such as sedimentation separation, pressure filtration, vacuum filtration, centrifugal filtration, decanter, etc., the resulting wet cake is dried by a known method to obtain zinc oxide and zinc hydroxide. A mixture is obtained.

【0005】[0005]

【発明の効果】本発明によれば、酸化亜鉛及び水酸化亜
鉛混合物と、水との分離性、例えば濾過性が良い(すな
わち濾過時の比抵抗α値が小さい)ので、分離に要する
時間を短縮できる。又、分離性が良いから、水を分離し
た後に得られるウエットケーキの含水率が低く、乾燥に
要する時間を短縮できる。即ち生産性良く酸化亜鉛及び
水酸化亜鉛混合物を製造することができる。また、該混
合物は塩基性塩類を含まず、高品質なのでそのままカ焼
により酸化亜鉛として単離した後、精錬して金属亜鉛と
することができる。
[Effects of the Invention] According to the present invention, the separation between the zinc oxide and zinc hydroxide mixture and water, for example, the filtration performance is good (that is, the specific resistance α value during filtration is small), so the time required for separation is reduced. Can be shortened. Furthermore, since the separability is good, the moisture content of the wet cake obtained after water separation is low, and the time required for drying can be shortened. That is, a mixture of zinc oxide and zinc hydroxide can be produced with high productivity. Furthermore, since the mixture does not contain basic salts and is of high quality, it can be directly isolated as zinc oxide by calcination, and then refined to obtain metallic zinc.

【0006】[0006]

【実施例】次に実施例をあげて本発明をさらに具体的に
説明するが、本発明はこれらの実施例によって何ら限定
されるものではない。 参考例1 反応釜(径1.5m)並びに反応釜の縦方向に設置され
た回転軸及びその下部に設けられた4枚羽根の傾斜型パ
ドル翼(θ=45°)を用いて次の反応および後処理を
行った〔但し、回転数150rpm、パドル翼の径と反
応釜の径との比=0.6〕。5−メチル  フルフラー
ル22.8kg、トルエン68.7kgおよび水86.
1kgを仕込み、この混合物中に、45℃で50%酢酸
5.4kg、亜鉛末23.1kgおよび2,3−ジクロ
ロ−1−プロペン32.4kgをそれぞれ同時並行的に
30分で添加した。添加終了後、反応が終了するまで同
温度で6時間撹拌した。反応終了後、濃塩酸19kgで
pH調製した。次いで反応釜底部の排出孔から反応混合
物を取り出し、不溶物を濾過により除去した。得られた
濾液を分液し、水層として亜鉛塩を含む酸性廃水(pH
=約4)143kgを得た。酸性廃水の分析結果は以下
のとおりであった。水分70.1重量%、塩化亜鉛26
.2重量%、酢酸亜鉛2.3重量%。
EXAMPLES Next, the present invention will be explained in more detail with reference to Examples, but the present invention is not limited to these Examples in any way. Reference Example 1 The following reaction was carried out using a reaction pot (diameter 1.5 m), a rotating shaft installed in the vertical direction of the reaction pot, and a four-bladed inclined paddle blade (θ = 45°) installed at the bottom of the rotating shaft. and post-treatment was carried out [however, the rotation speed was 150 rpm, and the ratio of the diameter of the paddle blade to the diameter of the reaction pot was 0.6]. 5-methyl furfural 22.8 kg, toluene 68.7 kg and water 86.
5.4 kg of 50% acetic acid, 23.1 kg of zinc powder, and 32.4 kg of 2,3-dichloro-1-propene were added simultaneously over 30 minutes to this mixture at 45°C. After the addition was completed, the mixture was stirred at the same temperature for 6 hours until the reaction was completed. After the reaction was completed, the pH was adjusted with 19 kg of concentrated hydrochloric acid. Next, the reaction mixture was taken out from the discharge hole at the bottom of the reaction vessel, and insoluble matter was removed by filtration. The obtained filtrate was separated, and the aqueous layer was acidic wastewater containing zinc salts (pH
= approx. 4) 143 kg was obtained. The analysis results of acidic wastewater were as follows. Moisture 70.1% by weight, zinc chloride 26%
.. 2% by weight, zinc acetate 2.3% by weight.

【0007】実施例1 27%苛性ソーダ水溶液12kg中に、参考例1で得た
亜鉛塩を含む酸性廃水20kgを24〜26℃で6時間
要して添加し、添加終了後、同温度で30分撹拌した(
反応終了時のpHは11.5であった)。酸化亜鉛及び
水酸化亜鉛混合物を、反応混合物から加圧濾過(濾過時
の比抵抗α=1.1×108 m/kg)により水と分
離してウエットケーキ5.2kgを得た(濾液中の亜鉛
イオン濃度は6mg/L)。このウエットケーキを乾燥
して4.2kgのドライケーキを得た(ウエットケーキ
中の固形分は80.6重量%)。また、ドライケーキの
平均粒子径(D50)は53μmであり、マイクロトラ
ックによる測定から、粒度分布は下記式で示されるRo
sin−Rammler分布式に従うことがわかった(
n =2.3、D*=58μm)。 R=100e −(D/D*) n 〔式中、Rはケーキの積算重量%、D はケーキの粒子
個々の径、 nは均一度、D*はr=e−1となるとき
のD で、 nに関係なく決定できる代表粒子径を表わ
す。〕尚、参考例1で得た亜鉛塩を含む酸性廃水の添加
時間θ(分)を変動させる以外は実施例1と同様にして
実験を繰返したところ、平均粒子径と添加時間について
次の関係式が得られた。 D50(μm)=−39.1376 +15.687 
logθ
Example 1 20 kg of the acidic wastewater containing the zinc salt obtained in Reference Example 1 was added to 12 kg of a 27% caustic soda aqueous solution at 24 to 26°C over a period of 6 hours, and after the addition was completed, the mixture was heated at the same temperature for 30 minutes. Stirred (
The pH at the end of the reaction was 11.5). The zinc oxide and zinc hydroxide mixture was separated from water by pressure filtration (specific resistance α during filtration = 1.1 x 108 m/kg) from the reaction mixture to obtain 5.2 kg of wet cake (in the filtrate). Zinc ion concentration is 6 mg/L). This wet cake was dried to obtain a 4.2 kg dry cake (solid content in the wet cake was 80.6% by weight). In addition, the average particle diameter (D50) of the dry cake is 53 μm, and the particle size distribution is expressed by the following formula as determined by Microtrack.
It was found that it follows the sin-Rammler distribution formula (
n = 2.3, D* = 58 μm). R = 100e - (D/D*) n [In the formula, R is the cumulative weight % of the cake, D is the diameter of each particle of the cake, n is the uniformity, and D* is the D when r = e-1. represents the representative particle diameter that can be determined regardless of n. ] The experiment was repeated in the same manner as in Example 1 except that the addition time θ (minutes) of the acidic wastewater containing zinc salt obtained in Reference Example 1 was varied, and the following relationship was found between the average particle diameter and addition time. The formula was obtained. D50 (μm) = -39.1376 +15.687
logθ

【0008】比較例1 反応温度を24〜26℃から59〜61℃に変える以外
は実施例1と同様に反応、濾過及び乾燥して次の結果を
得た。 濾過時の比抵抗α=1.1×1011m/kgドライケ
ーキ6.9kg(ウエットケーキ中の固形分は60.8
重量%)また、ドライケーキの粒度分布は2つの山を有
するバイモード型となり、微粒子側の平均粒子径(D5
0)は3.4μmであり、粗粒子側の平均粒子径(D5
0)は14μmであった(加重平均によるドライケーキ
全体のD50は9μm)。
Comparative Example 1 The reaction, filtration and drying were carried out in the same manner as in Example 1 except that the reaction temperature was changed from 24 to 26°C to 59 to 61°C to obtain the following results. Specific resistance α during filtration = 1.1 x 1011 m/kg Dry cake 6.9 kg (Solid content in wet cake is 60.8
In addition, the particle size distribution of the dry cake is bimodal with two peaks, and the average particle size on the fine particle side (D5
0) is 3.4 μm, and the average particle diameter on the coarse particle side (D5
0) was 14 μm (the weighted average D50 of the entire dry cake was 9 μm).

【0009】比較例2 亜鉛塩を含む酸性廃水の量を増やして反応終了時のpH
を8.0にする以外は実施例1と同様に反応及び濾過を
行って次の結果を得た。 濾液中の亜鉛イオン濃度=47mg/L
Comparative Example 2 The pH at the end of the reaction was increased by increasing the amount of acidic wastewater containing zinc salt.
The reaction and filtration were carried out in the same manner as in Example 1, except that the value was changed to 8.0, and the following results were obtained. Zinc ion concentration in filtrate = 47mg/L

【0010】比
較例3 亜鉛塩を含む酸性廃水の量を減らして反応終了時のpH
を13.0にする以外は実施例1と同様に反応及び濾過
を行って次の結果を得た。 濾液中の亜鉛イオン濃度=250mg/L
Comparative Example 3 The pH at the end of the reaction was adjusted by reducing the amount of acidic wastewater containing zinc salts.
The reaction and filtration were carried out in the same manner as in Example 1 except that the value was changed to 13.0, and the following results were obtained. Zinc ion concentration in filtrate = 250mg/L

【0011】
実施例2 下記組成の酸性廃水を用いる以外は実施例1と同様に反
応、濾過及び乾燥した。〔水分73重量%、塩化亜鉛2
6.2重量%〕実施例1と同様に、濾過時の比抵抗値(
α)の小さい、従って濾過性良好な酸化亜鉛及び水酸化
亜鉛混合物のけんだく液が得られ、濾液中の亜鉛イオン
濃度も6mg/L以下であった。
[0011]
Example 2 Reaction, filtration and drying were carried out in the same manner as in Example 1 except that acidic wastewater having the following composition was used. [Moisture 73% by weight, zinc chloride 2
6.2% by weight] Similar to Example 1, the specific resistance value during filtration (
A suspension of a mixture of zinc oxide and zinc hydroxide with a small α) and therefore good filterability was obtained, and the concentration of zinc ions in the filtrate was also 6 mg/L or less.

【0012】比較例4 亜鉛塩を含む酸性廃水中に、27%苛性ソーダ水溶液を
添加する以外は実施例1と同様に反応及び濾過を行って
次の結果を得た。
Comparative Example 4 The reaction and filtration were carried out in the same manner as in Example 1, except that a 27% aqueous solution of caustic soda was added to acidic wastewater containing zinc salts, and the following results were obtained.

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】苛性ソーダ又は苛性カリ水溶液中に亜鉛塩
を含む酸性廃水を添加して酸化亜鉛及び水酸化亜鉛混合
物を製造するバッチ式方法であって、且つ、反応終了時
のpHが約9.5 〜約12.5の範囲であることを特
徴とする方法。
1. A batch process for producing a mixture of zinc oxide and zinc hydroxide by adding acidic wastewater containing zinc salts to a caustic soda or caustic potash aqueous solution, and the pH at the end of the reaction is about 9.5. to about 12.5.
【請求項2】亜鉛塩として塩化亜鉛及び/又は酢酸亜鉛
を、酸性廃水中、約10〜約30重量%含む請求項1に
記載の方法。
2. A process according to claim 1, comprising from about 10 to about 30% by weight of zinc chloride and/or zinc acetate as the zinc salt in the acidic wastewater.
【請求項3】反応混合中の亜鉛塩濃度がZnとして約6
0g/L〜約110g/Lである請求項1または2に記
載の方法。
Claim 3: The concentration of zinc salt in the reaction mixture is about 6 as Zn.
3. The method of claim 1 or 2, wherein the amount is from 0 g/L to about 110 g/L.
【請求項4】反応温度が0℃〜40℃である請求項1乃
至3に記載の方法。
4. The method according to claim 1, wherein the reaction temperature is 0°C to 40°C.
【請求項5】酸性廃水の添加時間が約1〜約10時間で
ある請求項1乃至4に記載の方法。
5. The method of claim 1, wherein the acidic wastewater addition time is about 1 to about 10 hours.
JP09536991A 1991-04-25 1991-04-25 Method for producing zinc oxide and zinc hydroxide mixture Expired - Fee Related JP3185240B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP09536991A JP3185240B2 (en) 1991-04-25 1991-04-25 Method for producing zinc oxide and zinc hydroxide mixture

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP09536991A JP3185240B2 (en) 1991-04-25 1991-04-25 Method for producing zinc oxide and zinc hydroxide mixture

Publications (2)

Publication Number Publication Date
JPH04325414A true JPH04325414A (en) 1992-11-13
JP3185240B2 JP3185240B2 (en) 2001-07-09

Family

ID=14135715

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100401991B1 (en) * 1998-12-21 2003-12-18 주식회사 포스코 METHOD FOR RECYCLING SPENT Zn CLECTROYTE
CN102795658A (en) * 2012-07-30 2012-11-28 西安理工大学 Method for regulating zinc oxide crystal microstructure by using hydrogen peroxide
CN105366708A (en) * 2015-12-15 2016-03-02 清远先导材料有限公司 Method for producing aluminum zinc oxide by using zinc-containing waste liquid

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100401991B1 (en) * 1998-12-21 2003-12-18 주식회사 포스코 METHOD FOR RECYCLING SPENT Zn CLECTROYTE
CN102795658A (en) * 2012-07-30 2012-11-28 西安理工大学 Method for regulating zinc oxide crystal microstructure by using hydrogen peroxide
CN105366708A (en) * 2015-12-15 2016-03-02 清远先导材料有限公司 Method for producing aluminum zinc oxide by using zinc-containing waste liquid

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