JPS6058173B2 - Arsenic separation and recovery method - Google Patents
Arsenic separation and recovery methodInfo
- Publication number
- JPS6058173B2 JPS6058173B2 JP16563779A JP16563779A JPS6058173B2 JP S6058173 B2 JPS6058173 B2 JP S6058173B2 JP 16563779 A JP16563779 A JP 16563779A JP 16563779 A JP16563779 A JP 16563779A JP S6058173 B2 JPS6058173 B2 JP S6058173B2
- Authority
- JP
- Japan
- Prior art keywords
- arsenic
- organic solvent
- extraction
- sulfuric acid
- zinc
- 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
Links
- RQNWIZPPADIBDY-UHFFFAOYSA-N arsenic atom Chemical compound [As] RQNWIZPPADIBDY-UHFFFAOYSA-N 0.000 title claims description 87
- 229910052785 arsenic Inorganic materials 0.000 title claims description 80
- 238000000034 method Methods 0.000 title claims description 51
- 238000000926 separation method Methods 0.000 title description 5
- 238000011084 recovery Methods 0.000 title description 4
- 238000000605 extraction Methods 0.000 claims description 79
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 72
- 239000003960 organic solvent Substances 0.000 claims description 69
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 64
- 239000000243 solution Substances 0.000 claims description 39
- 229910052802 copper Inorganic materials 0.000 claims description 37
- 239000010949 copper Substances 0.000 claims description 37
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 36
- 229910052742 iron Inorganic materials 0.000 claims description 32
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 claims description 31
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims description 30
- 229910052793 cadmium Inorganic materials 0.000 claims description 30
- 229910052725 zinc Inorganic materials 0.000 claims description 30
- 239000011701 zinc Substances 0.000 claims description 30
- 239000002904 solvent Substances 0.000 claims description 13
- 125000000217 alkyl group Chemical group 0.000 claims description 9
- 125000004432 carbon atom Chemical group C* 0.000 claims description 8
- 238000005406 washing Methods 0.000 claims description 7
- 239000003929 acidic solution Substances 0.000 claims description 5
- 239000012670 alkaline solution Substances 0.000 claims description 5
- 125000004435 hydrogen atom Chemical group [H]* 0.000 claims description 5
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims description 4
- 229910017604 nitric acid Inorganic materials 0.000 claims description 4
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims description 3
- 150000002148 esters Chemical class 0.000 claims description 3
- 229910052739 hydrogen Inorganic materials 0.000 claims description 3
- 239000001257 hydrogen Substances 0.000 claims description 3
- LULLIKNODDLMDQ-UHFFFAOYSA-N arsenic(3+) Chemical compound [As+3] LULLIKNODDLMDQ-UHFFFAOYSA-N 0.000 claims 8
- 239000007788 liquid Substances 0.000 description 15
- 238000003723 Smelting Methods 0.000 description 10
- 238000004140 cleaning Methods 0.000 description 10
- 239000007789 gas Substances 0.000 description 9
- 238000000638 solvent extraction Methods 0.000 description 9
- GCPXMJHSNVMWNM-UHFFFAOYSA-N arsenous acid Chemical compound O[As](O)O GCPXMJHSNVMWNM-UHFFFAOYSA-N 0.000 description 7
- 230000008929 regeneration Effects 0.000 description 7
- 238000011069 regeneration method Methods 0.000 description 7
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 6
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- 229910001385 heavy metal Inorganic materials 0.000 description 6
- 239000003513 alkali Substances 0.000 description 5
- 239000007864 aqueous solution Substances 0.000 description 5
- 239000003085 diluting agent Substances 0.000 description 5
- KRHYYFGTRYWZRS-UHFFFAOYSA-N Fluorane Chemical compound F KRHYYFGTRYWZRS-UHFFFAOYSA-N 0.000 description 4
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 4
- 230000002378 acidificating effect Effects 0.000 description 4
- 229910052751 metal Inorganic materials 0.000 description 4
- 239000002184 metal Substances 0.000 description 4
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 3
- CUGMJFZCCDSABL-UHFFFAOYSA-N arsenic(3+);trisulfide Chemical compound [S-2].[S-2].[S-2].[As+3].[As+3] CUGMJFZCCDSABL-UHFFFAOYSA-N 0.000 description 3
- 238000002156 mixing Methods 0.000 description 3
- 229910000029 sodium carbonate Inorganic materials 0.000 description 3
- 238000005987 sulfurization reaction Methods 0.000 description 3
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 description 2
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 2
- UIIMBOGNXHQVGW-DEQYMQKBSA-M Sodium bicarbonate-14C Chemical compound [Na+].O[14C]([O-])=O UIIMBOGNXHQVGW-DEQYMQKBSA-M 0.000 description 2
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 2
- 239000001099 ammonium carbonate Substances 0.000 description 2
- 235000012501 ammonium carbonate Nutrition 0.000 description 2
- 238000007796 conventional method Methods 0.000 description 2
- 238000005868 electrolysis reaction Methods 0.000 description 2
- 150000002739 metals Chemical class 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 239000012074 organic phase Substances 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 235000017550 sodium carbonate Nutrition 0.000 description 2
- 235000011121 sodium hydroxide Nutrition 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- DJHGAFSJWGLOIV-UHFFFAOYSA-N Arsenic acid Chemical compound O[As](O)(O)=O DJHGAFSJWGLOIV-UHFFFAOYSA-N 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 238000005054 agglomeration Methods 0.000 description 1
- 230000002776 aggregation Effects 0.000 description 1
- 239000008346 aqueous phase Substances 0.000 description 1
- 150000004945 aromatic hydrocarbons Chemical class 0.000 description 1
- 229940000488 arsenic acid Drugs 0.000 description 1
- -1 arsenic ions Chemical class 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000002425 crystallisation Methods 0.000 description 1
- 230000008025 crystallization Effects 0.000 description 1
- 125000004122 cyclic group Chemical group 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 125000004119 disulfanediyl group Chemical group *SS* 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 239000002480 mineral oil Substances 0.000 description 1
- 239000011259 mixed solution Substances 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 150000003014 phosphoric acid esters Chemical class 0.000 description 1
- 238000005554 pickling Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 239000007790 solid phase Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000011550 stock solution Substances 0.000 description 1
- 210000002784 stomach Anatomy 0.000 description 1
- 150000003568 thioethers Chemical class 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Landscapes
- Inorganic Compounds Of Heavy Metals (AREA)
- Manufacture And Refinement Of Metals (AREA)
Description
【発明の詳細な説明】
本発明は、砒素■を含有する硫酸酸性溶液から砒素■を
回収する方法に関するものであり、特には非鉄金属製錬
における製錬排ガス洗浄工程で産出される稀薄硫酸のよ
うな、砒素■に加えて鉄■、亜鉛、銅、およびカドミウ
ムを含有する硫酸酸性溶液から溶媒抽出法により砒素■
を選択的に回収する方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for recovering arsenic from an acidic sulfuric acid solution containing arsenic. Arsenic is extracted by solvent extraction from a sulfuric acid acidic solution containing iron, zinc, copper, and cadmium in addition to arsenic.
The present invention relates to a method for selectively recovering .
非鉄金属製錬における製錬排ガス洗浄工程て産出される
稀薄硫酸、あるいは銅電解工程で産出される銅電解後液
、その他の廃液中にはかなりの量の砒素■が含まれてお
り、近時、公害対策上また副産物としての砒素■回収目
的のために、これら砒素■含有溶液から砒素■を回収す
る試みが為されている。Dilute sulfuric acid produced in the smelting exhaust gas cleaning process in non-ferrous metal smelting, the post-copper electrolysis solution produced in the copper electrolysis process, and other waste liquids contain a considerable amount of arsenic. Attempts have been made to recover arsenic from these arsenic-containing solutions for the purpose of preventing pollution and recovering arsenic as a by-product.
従来からの砒素回収法としては、硫化法により砒素を硫
化砒素とした後それぞれを戸別分離して回収し、水分を
約70%含む脱水ケーキとし、その後更に脱水および塊
状化処理を施すことによつて得られた塊体をビット内に
貯蔵することが行われていた。The conventional arsenic recovery method involves converting arsenic into arsenic sulfide using the sulfurization method, separating each product into a dehydrated cake containing about 70% water, and then subjecting it to further dehydration and agglomeration treatment. The resulting mass was stored in a bit.
この方法は簡便であるとは云え、大きな貯蔵スペースを
必要とする。最近、上記硫化法により得られた硫化砒素
を亜砒酸として回収する方法が提案されている。この方
法は、硫化法により生成された硫化砒素を酸化浸出し、
浸出液を還元後、濃縮および晶出を行うものであるが、
工程が長く複雑であり、面倒な操作を必要とする。更に
は、砒素■含有液中に砒素以外に鉄■、亜鉛、銅および
カドミウムが含まれる場合には、この方法は砒素■のみ
の分離回収方法としては好適ではな.い。上述した従来
法とは違つて、砒素■含有溶液から砒素■を直接回収し
うるなら、それに勝るものはない。Although this method is simple, it requires a large amount of storage space. Recently, a method has been proposed for recovering arsenic sulfide obtained by the above-mentioned sulfurization method as arsenous acid. This method involves oxidizing and leaching arsenic sulfide produced by the sulfurization method.
After reducing the leachate, it is concentrated and crystallized.
The process is long and complicated, and requires troublesome operations. Furthermore, if the arsenic-containing liquid contains iron, zinc, copper, and cadmium in addition to arsenic, this method is not suitable as a method for separating and recovering only arsenic. stomach. Unlike the conventional methods described above, if arsenic (2) can be directly recovered from an arsenic (1)-containing solution, there is no superior method.
これを可能ならしめるものとして溶媒抽出法と呼ばれる
方法がある。溶媒抽出法は、特定!の物質を選択的に抽
出しうる抽出剤を含む有機溶媒を使用して、その物質を
含む水溶液からそれを分離するものである。従つて、砒
素■含有水溶液からの砒素■の回収に溶媒抽出法を利用
するには、水溶液から砒素■イオンを選択的にしかも効
・率的に抽出しうる性能を具備する抽出剤を開発するこ
とが必要である。この場合、抽出剤は、砒素含有水溶液
と混らないことが必要であり、また抽出剤はその粘性を
低下せしめ、分散性を良くしそして接触効率を大きくす
るために稀釈剤で薄めて使用するのが一般的であるから
、稀釈剤によく溶けることも必要である。加えて、抽出
操作後逆抽出が行われるので、逆抽出操作を容易に行わ
しめることも必要である。更に、非鉄製錬工程において
産出する砒素■含有溶液中には砒素■以外に鉄■、亜鉛
、銅およびカドミウムが含まれており、抽出に際してこ
れら金属が不可避的に有機溶媒中に微量混入してくるの
で、抽出後溶媒からこれらノ金属を除去する対策も講じ
られねばならない。こうした様々の考慮事項の下で、本
発明者は、砒素■含有水溶液から溶媒抽出による砒素■
抽出のための抽出剤について多くの試行を重ねた結果、
ジアルキルジチオ燐酸エステル(アルキル基炭素数8〜
10)が上記抽出剤として好適に使用しうることを見出
した。この抽出剤は、砒素■に対する選択性にきわめて
秀れ、特に硫酸酸性溶液から99%以上の砒素■を抽出
しうる点で前述した目的に対して非常に秀れた抽出剤で
ある。斯くして、本発明は、砒素■、鉄■、亜鉛および
カドミウムを含有する硫酸酸性溶液を炭素数8〜10の
アルキル基を有するジアルキルジチオ燐酸エステルを抽
出剤として含む有機溶媒と、PH4以下て接触すること
からなる砒素の分離回収方法を提供する。本発明におい
て抽出剤として使用される炭素数8〜10のアルキル基
を持つジアルキルジチオ燐酸エステルは下記の構造式を
有する:(但しRは、8〜10の炭素数を持つアルキル
基であり、同一であつても異つてもよい。There is a method called solvent extraction method that makes this possible. Solvent extraction method is specific! An organic solvent containing an extractant capable of selectively extracting the substance is used to separate it from an aqueous solution containing the substance. Therefore, in order to use the solvent extraction method to recover arsenic from aqueous solutions containing arsenic, it is necessary to develop an extractant that has the ability to selectively and efficiently extract arsenic ions from aqueous solutions. It is necessary. In this case, the extractant needs to be immiscible with the arsenic-containing aqueous solution, and the extractant is diluted with a diluent to reduce its viscosity, improve dispersibility, and increase contact efficiency. Since it is common, it is also necessary that it dissolves well in diluents. In addition, since back-extraction is performed after the extraction operation, it is also necessary to easily perform the back-extraction operation. Furthermore, in addition to arsenic, the arsenic-containing solution produced in the nonferrous smelting process contains iron, zinc, copper, and cadmium, and trace amounts of these metals are inevitably mixed into the organic solvent during extraction. Therefore, measures must also be taken to remove these metals from the solvent after extraction. Under these various considerations, the present inventor has devised a method for extracting arsenic from an arsenic-containing aqueous solution by solvent extraction.
As a result of many trials with extractants for extraction,
Dialkyl dithiophosphate ester (alkyl group carbon number 8~
It has been found that 10) can be suitably used as the above-mentioned extractant. This extractant has excellent selectivity for arsenic (2), and is particularly excellent for the above-mentioned purpose in that it can extract 99% or more of arsenic (2) from an acidic sulfuric acid solution. Thus, the present invention provides an acidic sulfuric acid solution containing arsenic (1), iron (2), zinc and cadmium, an organic solvent containing as an extractant a dialkyldithiophosphate having an alkyl group of 8 to 10 carbon atoms, and a pH of 4 or lower. A method for separating and recovering arsenic is provided. The dialkyldithiophosphate ester having an alkyl group having 8 to 10 carbon atoms and used as an extractant in the present invention has the following structural formula: (R is an alkyl group having 8 to 10 carbon atoms, and the same It may be or be different.
)この抽出剤を使用しての砒素■の溶媒抽出に際して、
原料溶液中に含まれる鉄■、亜鉛、銅およびカドミウム
が不可避的に砒素抽出後の有機溶媒中に微量混入してく
る。) During the solvent extraction of arsenic using this extractant,
Trace amounts of iron, zinc, copper, and cadmium contained in the raw material solution inevitably become mixed into the organic solvent after arsenic extraction.
有機溶媒を再循環して使用するためにまた砒素■を単独
に分離回収するために、これらの微量混入してくる鉄■
、亜鉛、銅およびカドミウムを有機溶媒から除去するこ
とが必要である。このように、砒素■と共抽出される鉄
■、亜鉛、銅およびカドミウムのうち銅以外の重金属の
除去のためには、抽出後の溶媒を600y/′以下の硫
酸と接触させることがきわめて簡便な方法であることが
見出された。斯しくて、本発明はまた、抽出後溶媒を6
00f/e以下の濃度の硫酸溶液と接触して、該抽出後
溶媒に含まれる鉄■、亜鉛およびカドミウムを洗浄除去
することからなる砒素の分離回収方法をも提供する。こ
うして、鉄■、亜鉛およびカドミウムが除去された有機
溶媒は実質的に砒素■および銅のみを含むものであるが
、これから砒素■を回収しそして有機溶媒の循環使用を
可能ならしめるには、砒素を有機溶媒から逆抽出せねば
ならない。このような逆抽出操作には、炭酸ナトリウム
、炭酸アンモニウム、重炭酸ナトリウム、水酸化ナトリ
ウム等を代表とするアルカリ溶液が好適に使用されうる
。従つて、本発明は、前述のようにして鉄■、亜鉛およ
びカドミウムを除去した後の砒素■および銅を含有する
有機溶媒をアルカリで逆抽出することをも含む砒素の分
離回収方法をも提供する。この場合、アルカリ溶液のア
ルカリ濃度は0.01〜5モルの範囲とすることが好ま
しい。この操作においては有機溶媒中の銅は逆抽出工程
に移行しない。上述したアルカリによる逆抽出操作にお
いて、逆抽出後の有機溶媒はアルカリ型となつているか
ら有機溶媒の循環使用のためには水素型に変換しておか
なければならない。In order to recycle and use the organic solvent and separate and recover the arsenic, these small amounts of iron are removed.
, it is necessary to remove zinc, copper and cadmium from organic solvents. In this way, in order to remove heavy metals other than copper among the iron (2), zinc, copper and cadmium that are co-extracted with arsenic (1), it is extremely convenient to contact the solvent after extraction with 600y/' or less of sulfuric acid. It was discovered that this is a method. Thus, the present invention also provides that after extraction the solvent is
A method for separating and recovering arsenic is also provided, which comprises contacting with a sulfuric acid solution having a concentration of 00 f/e or less to wash and remove iron, zinc and cadmium contained in the solvent after the extraction. In this way, the organic solvent from which iron, zinc, and cadmium have been removed essentially contains only arsenic and copper. However, in order to recover arsenic from this and make it possible to recycle the organic solvent, it is necessary to convert arsenic into an organic solvent. It must be back extracted from the solvent. For such a back extraction operation, an alkaline solution typified by sodium carbonate, ammonium carbonate, sodium bicarbonate, sodium hydroxide, etc. can be suitably used. Therefore, the present invention also provides a method for separating and recovering arsenic, which includes back-extracting the organic solvent containing arsenic and copper with an alkali after removing iron, zinc, and cadmium as described above. do. In this case, the alkaline concentration of the alkaline solution is preferably in the range of 0.01 to 5 mol. In this operation, copper in the organic solvent is not transferred to the back extraction step. In the above-mentioned back-extraction operation using alkali, the organic solvent after back-extraction is in an alkaline form, so it must be converted into a hydrogen form in order to reuse the organic solvent.
これは、硫酸と接触することによつて容易にもたらされ
る。斯くして、本発明は、また別の様相において、前記
アルカリによる逆抽出後の有機溶媒を600y/e以下
の濃度の硫酸溶液と接触して、有機溶媒をアルカリ型か
ら水素型に変換することを含む砒素の分離回収方法を提
供する。さらに本発明は有機溶媒に抽出された銅が有機
溶媒の循環使用中に蓄積することによる砒素■の抽出能
力の低下を防止するために、前記水素型に変換した有機
溶媒の一部または全部を600y/e以下の濃度の硝酸
溶液と接触することにより銅および砒素■の他の微量の
鉄■、亜鉛およびカドミウムを除去することを含む砒素
の分離回収方法を提供する。This is easily effected by contacting with sulfuric acid. Thus, in another aspect of the present invention, the organic solvent after back extraction with alkali is contacted with a sulfuric acid solution having a concentration of 600 y/e or less to convert the organic solvent from an alkaline type to a hydrogen type. Provided is a method for separating and recovering arsenic containing arsenic. Furthermore, in order to prevent the copper extracted into the organic solvent from accumulating during the cyclic use of the organic solvent and the ability to extract arsenic from decreasing, part or all of the organic solvent converted to the hydrogen form is removed. Provided is a method for separating and recovering arsenic, which includes removing trace amounts of iron, zinc, and cadmium in addition to copper and arsenic by contacting with a nitric acid solution having a concentration of 600 y/e or less.
以下、本発明を、非鉄製錬における製錬排ガス洗浄工程
から生ずる稀薄硫酸からの砒素■の回収に基いて、添付
図面のフローシートを参照しつつ具体的に説明する。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be specifically described below, based on the recovery of arsenic (2) from dilute sulfuric acid generated from a smelting exhaust gas cleaning process in non-ferrous smelting, with reference to the flow sheet of the attached drawings.
非鉄製錬のガス洗浄工程から生ずる稀薄硫酸溶液は、ガ
スの出所源が硫化鉱石の製錬排ガスかあるいは硫化鉱石
の焙焼ガスかと云つたプロセスによつて異なるが、一般
に5〜300V/′の濃度の硫酸を含有しそして0.5
〜30y/eの濃度の砒素■と、その他鉄、亜鉛、銅お
よびカドミウム等の重金属ならびに塩酸や弗酸等を含ん
でいる。The dilute sulfuric acid solution generated from the gas cleaning process in nonferrous smelting generally has a voltage of 5 to 300 V/', although the source of the gas varies depending on the process, such as whether the gas is smelted exhaust gas from sulfide ore or roasted gas from sulfide ore. containing sulfuric acid at a concentration of 0.5
It contains arsenic (2) at a concentration of ~30 y/e, other heavy metals such as iron, zinc, copper, and cadmium, and hydrochloric acid and hydrofluoric acid.
いずれにせよ、このような稀薄硫酸溶液は本発明に従つ
てフローシートでは左端に抽出工程1として示される工
程において溶媒抽出処理を受ける。所望なら、爾後の洗
浄工程から生ずる後液を混合してもよい(後述)。抽出
工程1においては、前記砒素■その他を含有する稀薄硫
酸溶液と有機溶媒との接触が行われ、その結果溶液中の
砒素■および銅の全量ならびに鉄■、亜鉛およびカドミ
ウムの一部は有機溶媒中に移行し、抽出後液1が生成す
る。この場合特に鉄■は溶液の硫酸濃度が高くなるとほ
とんど抽出されない。有機溶媒は初回は新しいものが使
用されるが、その後は後述するようにして使用ずみ有機
溶媒が循環再使用される。有機溶媒は、前述した炭素数
8〜10のアルキル基を有するジアルキルジチオ燐酸エ
ステル抽出剤を希釈剤に溶かしたものである。希釈剤と
しては、パラフィン系、ナフテン系および芳香族系の炭
化水素である鉱油の中から単独であるいは混合下で適宜
選択して使用される。接触操作は、周知のミキサ・セト
ラー、抽出塔、遠心抽出機等を使用しバッチ式でも連続
式でも行いうる。混合温度は使用する希釈剤に依存する
が、30。〜80℃、好ましくは40剤〜60℃に選定
される。有機相(有機溶媒)対水相(被処理液)の接触
時の容積比(以下0/A比という)は、1115〜5ハ
程度、好ましくは112〜2ハであり、使用する設備お
よび操業条件に応じて適宜選択されうる。接触時間は、
接触効率に依存するが、2〜3吟、通常5〜1吟程度で
十分である。図面のフローシートにおいては、抽出工程
1に加えて抽出工程2が設けられている。In any case, such a dilute sulfuric acid solution is subjected to a solvent extraction process in accordance with the present invention in a step shown as extraction step 1 at the far left in the flow sheet. If desired, the after-liquid resulting from the subsequent washing step may be mixed (described below). In extraction step 1, the dilute sulfuric acid solution containing arsenic and others is brought into contact with an organic solvent, and as a result, the total amount of arsenic and copper in the solution and a portion of iron, zinc and cadmium are removed from the organic solvent. The post-extraction liquid 1 is produced. In this case, iron (2) in particular is hardly extracted when the sulfuric acid concentration of the solution becomes high. A new organic solvent is used for the first time, but after that, the used organic solvent is recycled and reused as described below. The organic solvent is a solution of the aforementioned dialkyldithiophosphate extractant having an alkyl group having 8 to 10 carbon atoms in a diluent. As the diluent, paraffinic, naphthenic and aromatic hydrocarbon mineral oils may be used alone or in combination. The contact operation can be carried out either batchwise or continuously using well-known mixers/settlers, extraction towers, centrifugal extractors, and the like. The mixing temperature depends on the diluent used, but is 30°C. The temperature is selected to be 80°C to 80°C, preferably 40°C to 60°C. The volume ratio of the organic phase (organic solvent) to the aqueous phase (liquid to be treated) at the time of contact (hereinafter referred to as 0/A ratio) is about 1115 to 5 ha, preferably 112 to 2 ha, and depends on the equipment and operation used. It can be selected as appropriate depending on the conditions. The contact time is
Although it depends on the contact efficiency, 2 to 3 gin, usually 5 to 1 gin, is sufficient. In the flow sheet of the drawing, an extraction step 2 is provided in addition to the extraction step 1.
この抽出工程2は、後述する逆抽出後液から砒素■を亜
砒酸として晶析した後の後液中に微量含まれる砒素を完
全に抽出除去するためのものである。抽出工程2は抽出
工程1からの有機溶媒を使用して通常実施されるが、抽
出工程1を経ない有機溶媒を使用することも何等差支え
ない。抽出工程1からの抽出後液1は、砒素をほとんど
含有せす重金属をわすかに含むものであり、含有する塩
酸および弗酸の濃度にもよるが、必要に応じて例えば酸
洗い工程と云つた他の工程部門において硫酸として有効
に再利用される。This extraction step 2 is for completely extracting and removing a trace amount of arsenic contained in the liquid after arsenic (1) is crystallized as arsenous acid from the liquid after back extraction, which will be described later. Although extraction step 2 is usually carried out using the organic solvent from extraction step 1, there is no problem in using an organic solvent that has not been passed through extraction step 1. The post-extraction solution 1 from extraction step 1 contains almost all arsenic and a slight amount of heavy metals, and depending on the concentration of hydrochloric acid and hydrofluoric acid contained therein, it may be subjected to a pickling step, for example, if necessary. It can be effectively recycled as sulfuric acid in other process departments.
有効利用できない場合には、抽出工程2から生ずる抽出
後液2と共にアルカリの添加による通常の中和処理を経
て放流される。抽出工程1からのまた必要に応じ抽出工
程2を経た後の砒素■および銅の全量ならびに鉄■、亜
鉛およびカドミウムの一部を抽出した抽出後有機溶媒は
、こうして砒素■と共に共抽出された鉄■、亜鉛および
カドミウムを除去するべく洗浄工程に送られる。If it cannot be used effectively, it is discharged together with the post-extraction liquid 2 resulting from the extraction step 2 through a normal neutralization process by adding alkali. The post-extraction organic solvent that has extracted the total amount of arsenic and copper from extraction step 1 and optionally after extraction step 2 as well as a portion of iron, zinc and cadmium contains the iron thus co-extracted with arsenic. (2) Sent to a cleaning process to remove zinc and cadmium.
洗浄工程は、抽出後有機溶媒を600y/e以下、好ま
しくは100〜400y/eの濃度の硫酸溶液と接触す
ることにより実施される。洗浄工程における有機相と硫
酸溶液の接触は、111〜1511,,好ましくは51
1〜10ハのO/A比において行われ、そして混合温度
、接触時間および使用設備等の他の条件については抽出
工程と同様にして適宜選択される。洗浄工程からの処理
後液は、単独に処理してもよいが、好ましくは前述した
通り抽出工程1に繰返される。洗浄工程において鉄■、
亜鉛およびカドミウムが除去された後の砒素■含有有機
溶媒は次いで、逆抽出工程において逆抽出操作を受ける
。The washing step is carried out by contacting the organic solvent after extraction with a sulfuric acid solution having a concentration of 600 y/e or less, preferably 100 to 400 y/e. The contact between the organic phase and the sulfuric acid solution in the washing step is from 111 to 1511, preferably 51
It is carried out at an O/A ratio of 1 to 10 Ha, and other conditions such as mixing temperature, contact time and equipment used are appropriately selected in the same manner as in the extraction step. The processed liquid from the washing step may be processed alone, but is preferably repeated in extraction step 1 as described above. In the cleaning process, iron■,
The arsenic-containing organic solvent after zinc and cadmium has been removed is then subjected to a back extraction operation in a back extraction step.
逆抽出工程において、砒素含有有機溶媒は、炭酸ナトリ
ウム、炭酸アンモニウム、重炭酸ナトリウム、水酸化ナ
トリウム等を代表とするアルカリ単一溶液あるいは混合
溶液てもつて砒素が逆抽出される。逆抽出を最適に行う
ためのアルカリ濃度は0.01〜.5モルとされる。逆
抽出条件としては、O/A比は113〜101L好まし
くは111〜5ハとされ、そして混合温度、接触時間お
よび使用設備は抽出工程と同様に選択できる。逆抽出工
程においては、砒素■が除去された有.機溶媒と砒素■
を含有する逆抽出後液が生ずる。In the back-extraction step, arsenic is back-extracted from the arsenic-containing organic solvent using a single alkali solution or a mixed solution of sodium carbonate, ammonium carbonate, sodium bicarbonate, sodium hydroxide, and the like. The alkaline concentration for optimal back extraction is 0.01~. It is said to be 5 moles. As for the back extraction conditions, the O/A ratio is 113 to 101 L, preferably 111 to 5 H, and the mixing temperature, contact time and equipment used can be selected in the same manner as in the extraction process. In the back-extraction process, the arsenic is removed. Organic solvent and arsenic ■
A back-extraction solution containing .
逆抽出後液は、通常硫酸を添加して硫酸酸性にした後必
要に応じて設けた晶析工程で砒素を亜砒酸として析出さ
せ、更にフィルターブレスや遠心分離等によつて固相の
亜砒酸を液体から分離する分・離工程において亜砒酸を
回収する。分離工程における亜砒酸分離後液は、先きの
抽出工程2において処理される原液として再処理されう
る。設備の状況に応じては、抽出工程2を省略して抽出
工程1のみとなし、亜砒酸分離後液を抽出工程1に繰返
すこともできる。この液中における微量の砒素■は抽出
工程2において抽出される。逆抽出工程を経た有機溶媒
は、次いで有機溶媒再生工程1において、有機溶媒のア
ルカリ型を600g/′以下、好ましくは50〜300
g/eの濃度の硫酸溶液で水素型に変換するべく処理さ
れる。The solution after back extraction is usually made acidic by adding sulfuric acid, and then arsenic is precipitated as arsenous acid in a crystallization step provided as necessary, and the solid phase arsenous acid is further converted into a liquid by filter press or centrifugation. Arsenous acid is recovered in the separation process. The liquid after arsenous acid separation in the separation step can be reprocessed as a stock solution to be processed in the extraction step 2 above. Depending on the situation of the equipment, extraction step 2 can be omitted and only extraction step 1 is performed, and the liquid after arsenous acid separation can be repeated in extraction step 1. A trace amount of arsenic (3) in this liquid is extracted in extraction step 2. The organic solvent that has undergone the back extraction step is then subjected to an organic solvent regeneration step 1 in which the alkaline form of the organic solvent is reduced to 600 g/' or less, preferably 50 to 300 g/'.
It is treated with a sulfuric acid solution at a concentration of g/e to convert it into the hydrogen form.
有機溶媒再生工程1において再生を終えた有機溶媒の一
部は抽出工程1に循環して再使用される。ノ有機溶媒再
生工程1における後液は、ごく微量の砒素を含んでいる
ので抽出工程1あるいは2に送り、砒素を回収する。抽
出工程1で有機溶媒に抽出された銅は有機溶媒再生工程
1までの間に有機溶媒から除去されないので、次の有機
溶媒再生工程2において有機溶媒の一部または全部60
0y/l以下の濃度の硝酸溶液と接触し、銅を洗浄除去
して有機溶媒を再生する。A part of the organic solvent that has been regenerated in the organic solvent regeneration step 1 is recycled to the extraction step 1 and reused. Since the liquid after organic solvent regeneration step 1 contains a very small amount of arsenic, it is sent to extraction step 1 or 2 to recover arsenic. Since the copper extracted into the organic solvent in extraction step 1 is not removed from the organic solvent until organic solvent regeneration step 1, part or all of the organic solvent is removed in the next organic solvent regeneration step 2.
It is contacted with a nitric acid solution having a concentration of 0 y/l or less to wash away the copper and regenerate the organic solvent.
こうして再生された有機溶媒は抽出工程1へ循環して再
使用される。この工程で処理された処理後液には銅の他
に微量の鉄、亜鉛、カドミウムおよび砒素が含まれてい
るので、硫化剤を添加する周知の方法によりこれら成分
のうち少くとも銅を硫化物として沈澱除去した後、該澱
物を銅製錬工程へ繰り返す。硫化物として沈澱除去され
なかつた銅以外の成分を含む液は必要に応じて、抽出工
程1もしくは抽出工程2において処理することができる
。以上説明したように、有機溶媒は、抽出工程1におい
て、また必要なら抽出工程2において砒素■および銅の
全量ならびに鉄■、亜鉛、およびカドミウムの重金属の
一部が抽出された後、洗浄工程において鉄■、亜鉛およ
びカドミウムが除去され、次いで逆抽出工程において残
つた砒素■が逆抽出されそして有機溶媒再生工程1にお
いてアルカリ型から水素型に変換される。The organic solvent thus regenerated is recycled to extraction step 1 and reused. Since the treated solution treated in this process contains trace amounts of iron, zinc, cadmium, and arsenic in addition to copper, at least the copper of these components is converted into sulfide by the well-known method of adding a sulfiding agent. After removing the precipitate, the precipitate is repeated to the copper smelting process. The liquid containing components other than copper that have not been precipitated and removed as sulfides can be treated in extraction step 1 or extraction step 2, if necessary. As explained above, the organic solvent is used in the washing step after the total amount of arsenic and copper and part of the heavy metals of iron, zinc, and cadmium are extracted in the extraction step 1 and, if necessary, in the extraction step 2. Iron (2), zinc and cadmium are removed, and then the remaining arsenic (2) is back extracted in the back extraction step and converted from the alkaline form to the hydrogen form in the organic solvent regeneration step (1).
そして最後に有機溶媒再生工程2において有機溶媒に蓄
積する銅が除去され、有機溶媒は完全に再生された状態
で抽出工程1に循環される。逆抽出工程で逆抽出される
砒素■は重金属が既に除去ずみであるから高純度で回収
される。以下、実施例を示す。Finally, in the organic solvent regeneration step 2, the copper accumulated in the organic solvent is removed, and the organic solvent is recycled to the extraction step 1 in a completely regenerated state. Since the heavy metals have already been removed from the arsenic (2) that is back-extracted in the back-extraction process, it can be recovered with high purity. Examples are shown below.
実施例1
銅製錬工程から発生する亜硫酸ガスの洗浄工程て産出す
る表−1の組成をもつ稀薄硫酸溶液からディスパーゾル
(シェル化学(株)の商品名)で20%に希釈したジー
2エチルヘキシルジチオ燐酸エステルからなる有機溶媒
を用いて砒素■を回収する試験を行つた。Example 1 Di-2-ethylhexyl dithio diluted to 20% with dispersol (trade name of Shell Chemical Co., Ltd.) from a dilute sulfuric acid solution having the composition shown in Table 1 produced in the process of cleaning sulfur dioxide gas generated from the copper smelting process. A test was conducted to recover arsenic (2) using an organic solvent consisting of phosphoric acid ester.
溶媒抽出操作は、次の条件を用いて実施した。The solvent extraction operation was performed using the following conditions.
0/A:1ハ、温度:50℃、接触方式:攪拌式(75
0rpm×1紛)。0/A: 1c, temperature: 50°C, contact method: stirring method (75
0 rpm x 1 powder).
得られた抽出後液の組成は砒素■0.001y/e1鉄
■0.023y/′、亜鉛0.136ダ/′、銅0.0
01y/e以下およびカドミウム0.115y/eであ
り、実に99.9%以上の砒素■抽出率を示した。The composition of the obtained post-extraction solution is: Arsenic: 0.001y/e1 Iron: 0.023y/', Zinc: 0.136d/', Copper: 0.0
01y/e or less and cadmium 0.115y/e, showing an arsenic extraction rate of 99.9% or more.
本例においては、硫酸濃度が比較的高いため、鉄および
カドミウムはほとんど抽出されなかつた。一方銅は99
.9%以上抽出された。実施例2
抽出剤としてジ3,5,5−トリメチルヘキシルジチオ
燐酸エステルおよびジイソデシルジチオ燐酸エステルを
使用して実施例1と同じ条件て抽出試験を行つた。In this example, iron and cadmium were hardly extracted due to the relatively high sulfuric acid concentration. On the other hand, copper is 99
.. More than 9% was extracted. Example 2 An extraction test was conducted under the same conditions as in Example 1 using di3,5,5-trimethylhexyldithiophosphate and diisodecyldithiophosphate as extractants.
いずれも、99%以上の高い砒素抽出率を示した。実施
例3
実施例1において得られた抽出後有機溶媒を洗浄処理し
た。All showed a high arsenic extraction rate of 99% or more. Example 3 The post-extraction organic solvent obtained in Example 1 was washed.
洗浄処理は300y/′の硫酸を用いて5ハのO/A比
を使用して実施した。洗浄効果は次の通りであつた。次
いで、洗浄後の有機溶媒から53y/eの濃度の炭酸ナ
トリウム溶液を用いて砒素を逆抽出した。The cleaning process was carried out using 300y/' sulfuric acid and an O/A ratio of 5ha. The cleaning effects were as follows. Next, arsenic was back-extracted from the washed organic solvent using a sodium carbonate solution with a concentration of 53 y/e.
逆抽出条件はO/A比=1′2、温度50℃そして接触
時間1紛とした。その結果98.7%の逆抽出率が得ら
れた。逆抽出操作において有機溶媒中の銅はまだ有機溶
媒中に残つているので、上記逆抽出後、100ダ/eの
濃度の硫酸溶液でアルカリ型から水素型へ変換処理した
有機溶媒を126f/′の濃度の硝酸溶液とO/A比、
112、温度50℃、接触時間30分の条件で接触させ
ることにより有機溶媒から銅を除去した。The back extraction conditions were O/A ratio = 1'2, temperature 50°C, and contact time 1 powder. As a result, a back extraction rate of 98.7% was obtained. In the back extraction operation, the copper in the organic solvent still remains in the organic solvent, so after the above back extraction, the organic solvent converted from alkaline type to hydrogen type with a sulfuric acid solution with a concentration of 100 da/e was converted to 126 f/'. Nitric acid solution with concentration and O/A ratio,
112, copper was removed from the organic solvent by contacting at a temperature of 50° C. and a contact time of 30 minutes.
その結果90%の脱銅率が得られた。As a result, a copper removal rate of 90% was obtained.
かくして、本発明によれば、具体例で示したように、非
鉄金属製錬における製錬排ガス洗浄工程より産生する稀
薄硫酸中の砒素を溶媒抽出によつて抽出分離し、硫酸に
よる洗浄工程をもうけることによつて逆抽出液から重金
属の含有されない高純度の亜砒酸を回収する方法か確立
されたこととなり、従来法に比べてきわめて効果的かつ
簡単に砒素の回収を行いうるので工業的意義はきわめて
゛大きい。Thus, according to the present invention, as shown in the specific example, arsenic in dilute sulfuric acid produced from the smelting exhaust gas cleaning process in nonferrous metal smelting is extracted and separated by solvent extraction, and a cleaning process with sulfuric acid is added. As a result, a method has been established for recovering high-purity arsenic acid that does not contain heavy metals from the back-extraction solution, and as it is extremely effective and easy to recover arsenic compared to conventional methods, it has great industrial significance. It's so big.
図面は、本発明の一具体例に従う砒素回収工程のフロー
シートである。The drawing is a flow sheet of an arsenic recovery process according to one embodiment of the present invention.
Claims (1)
する硫酸酸性溶液を炭素数8〜10のアルキル基を有す
るジアルキルジチオ燐酸エステルを抽出剤として含む有
機溶媒と、pH4以下で接触することからなる砒素の分
離回収方法。 2 砒素III、鉄II、亜鉛、銅およびカドミウムを含有
する硫酸酸性溶液を炭素数8〜10のアルキル基を有す
るジアルキルジチオ燐酸エステルを抽出剤として含む有
機溶媒とpH4以下で接触し、そして抽出後溶媒を60
0g/l以下の濃度の硫酸溶液と接触して該抽出後溶媒
に含まれる鉄II、亜鉛およびカドミウムを洗浄除去する
ことなる砒素の分離回収方法。 3 砒素III、鉄II、亜鉛、銅およびカドミウムを含有
する硫酸酸性溶液を炭素数8〜10のアルキル基を有す
るジアルキルジチオ燐酸エステルを抽出剤として含む有
機溶媒とpH4以下で接触し、そして抽出後溶媒を60
0g/l以下の濃度の硫酸溶液と接触して該抽出後溶媒
に含まれる鉄II、亜鉛およびカドミウムを洗浄除去し、
次いで砒素IIIを含有する有機溶媒をアルカリ溶液で逆
抽出することから砒素の分離回収方法。 4 砒素III、鉄II、亜鉛、銅およびカドミウムを基を
有するジアルキルジチオ燐酸エステルを抽出剤として含
む有機溶媒とpH4以下で接触し、そして抽出後溶媒を
600g/l以下の濃度の硫酸溶液と接触して該抽出後
溶媒に含まれる鉄II、亜鉛およびカドミウムを洗浄除去
し、次いで砒素IIIを含有する上記洗浄後の有機溶媒を
アルカリ溶液で逆抽出し、然かる後該逆抽出後の有機溶
媒を600g/l以下の濃度の硫酸溶液と接触して有機
溶媒をアルカリ型から水素型に変換することなる砒素の
分離回収方法。 5 砒素III、鉄II、亜鉛、銅およびカドミウムを含有
する硫酸酸性溶液を炭素数8〜10のアルキル基を有す
るジアルキルジチオ燐酸エステルを抽出剤として含む有
機溶媒とpH4以下で接触し、そして抽出後溶媒を60
0g/l以下の濃度の硫酸溶液と接触して該抽出後溶媒
に含まれる鉄II、亜鉛およびカドミウムを洗浄除去し、
次いで砒素IIIを含有する上記洗浄後の有機溶媒をアル
カリ溶液で逆抽出し、然かる後該抽出後の有機溶媒を6
00g/l以下の濃度の硫酸溶液と接触することにより
、アルカリ型から水素型に変換した有機溶媒の一部また
は全部を600g/l以下の濃度の硝酸溶液と接触して
有機溶媒に蓄積している銅並びに微量の鉄、亜鉛および
カドミウムを洗浄除去することからなる砒素の分離回収
方法。[Scope of Claims] 1. A sulfuric acid acidic solution containing arsenic III, iron II, zinc, copper and cadmium is mixed with an organic solvent containing a dialkyldithiophosphate having an alkyl group having 8 to 10 carbon atoms as an extractant, and a pH of 4 or less. A method for separating and recovering arsenic, which involves contacting with arsenic. 2. A sulfuric acid acidic solution containing arsenic III, iron II, zinc, copper and cadmium is brought into contact with an organic solvent containing a dialkyldithiophosphate having an alkyl group having 8 to 10 carbon atoms as an extractant at a pH of 4 or less, and after extraction. 60% solvent
A method for separating and recovering arsenic, which comprises contacting with a sulfuric acid solution having a concentration of 0 g/l or less to wash and remove iron II, zinc and cadmium contained in the solvent after the extraction. 3. A sulfuric acid acidic solution containing arsenic III, iron II, zinc, copper and cadmium is brought into contact with an organic solvent containing a dialkyldithiophosphate having an alkyl group having 8 to 10 carbon atoms as an extractant at a pH of 4 or less, and after extraction. 60% solvent
Contact with a sulfuric acid solution having a concentration of 0 g/l or less to wash and remove iron II, zinc and cadmium contained in the extracted solvent,
Next, the organic solvent containing arsenic III is back-extracted with an alkaline solution to separate and recover arsenic. 4 Contact with an organic solvent containing as an extractant a dialkyldithiophosphate ester having arsenic III, iron II, zinc, copper and cadmium groups at a pH below 4, and after extraction contact the solvent with a sulfuric acid solution having a concentration below 600 g/l. After the extraction, iron II, zinc, and cadmium contained in the solvent are washed away, and then the organic solvent containing arsenic III after washing is back-extracted with an alkaline solution, and then the organic solvent after the back-extraction is A method for separating and recovering arsenic, which comprises contacting arsenic with a sulfuric acid solution having a concentration of 600 g/l or less to convert an organic solvent from an alkaline type to a hydrogen type. 5. A sulfuric acid acidic solution containing arsenic III, iron II, zinc, copper and cadmium is brought into contact with an organic solvent containing a dialkyldithiophosphate having an alkyl group having 8 to 10 carbon atoms as an extractant at a pH of 4 or below, and after extraction. 60% solvent
Contact with a sulfuric acid solution having a concentration of 0 g/l or less to wash and remove iron II, zinc and cadmium contained in the extracted solvent,
Next, the washed organic solvent containing arsenic III is back-extracted with an alkaline solution, and then the extracted organic solvent is extracted with 6
Part or all of the organic solvent converted from alkaline form to hydrogen form by contacting with a sulfuric acid solution having a concentration of 00 g/l or less is accumulated in the organic solvent by contacting with a nitric acid solution having a concentration of 600 g/l or less. A method for separating and recovering arsenic, which consists of washing and removing copper and trace amounts of iron, zinc and cadmium.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP16563779A JPS6058173B2 (en) | 1979-12-21 | 1979-12-21 | Arsenic separation and recovery method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP16563779A JPS6058173B2 (en) | 1979-12-21 | 1979-12-21 | Arsenic separation and recovery method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5688827A JPS5688827A (en) | 1981-07-18 |
| JPS6058173B2 true JPS6058173B2 (en) | 1985-12-18 |
Family
ID=15816138
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP16563779A Expired JPS6058173B2 (en) | 1979-12-21 | 1979-12-21 | Arsenic separation and recovery method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6058173B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6362187U (en) * | 1986-10-09 | 1988-04-25 |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106390355B (en) * | 2016-08-31 | 2019-07-12 | 航天凯天环保科技股份有限公司 | A kind of preparation method and application of modification secondary zinc oxide slag composite particles that consolidating arsenic for arsenic alkaline slag |
-
1979
- 1979-12-21 JP JP16563779A patent/JPS6058173B2/en not_active Expired
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6362187U (en) * | 1986-10-09 | 1988-04-25 |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5688827A (en) | 1981-07-18 |
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