JPH086150B2 - Method for separating and recovering valuable metals from manganese nodules or cobalt crusts - Google Patents
Method for separating and recovering valuable metals from manganese nodules or cobalt crustsInfo
- Publication number
- JPH086150B2 JPH086150B2 JP22950986A JP22950986A JPH086150B2 JP H086150 B2 JPH086150 B2 JP H086150B2 JP 22950986 A JP22950986 A JP 22950986A JP 22950986 A JP22950986 A JP 22950986A JP H086150 B2 JPH086150 B2 JP H086150B2
- Authority
- JP
- Japan
- Prior art keywords
- separating
- precipitate
- filtrate
- separated
- cobalt
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- 239000011572 manganese Substances 0.000 title claims description 34
- 238000000034 method Methods 0.000 title claims description 27
- 229910052748 manganese Inorganic materials 0.000 title claims description 22
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 title claims description 8
- 229910052751 metal Inorganic materials 0.000 title claims description 8
- 239000002184 metal Substances 0.000 title claims description 8
- 150000002739 metals Chemical class 0.000 title claims description 6
- 241001283150 Terana caerulea Species 0.000 title claims description 5
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 36
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims description 21
- 229910052802 copper Inorganic materials 0.000 claims description 19
- 239000010949 copper Substances 0.000 claims description 19
- 229910052759 nickel Inorganic materials 0.000 claims description 18
- 229910052742 iron Inorganic materials 0.000 claims description 15
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 claims description 13
- 239000000706 filtrate Substances 0.000 claims description 13
- 101100513612 Microdochium nivale MnCO gene Proteins 0.000 claims description 11
- 239000002244 precipitate Substances 0.000 claims description 8
- 230000003647 oxidation Effects 0.000 claims description 6
- 238000007254 oxidation reaction Methods 0.000 claims description 6
- 238000001914 filtration Methods 0.000 claims description 5
- 230000002378 acidificating effect Effects 0.000 claims description 4
- 230000001590 oxidative effect Effects 0.000 claims description 4
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 claims description 3
- 235000012501 ammonium carbonate Nutrition 0.000 claims description 3
- 239000001099 ammonium carbonate Substances 0.000 claims description 3
- 239000000203 mixture Substances 0.000 claims description 3
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 claims description 2
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N ammonia Natural products N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 2
- 150000003863 ammonium salts Chemical class 0.000 claims description 2
- 229910017052 cobalt Inorganic materials 0.000 claims description 2
- 239000010941 cobalt Substances 0.000 claims description 2
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 claims description 2
- 238000009854 hydrometallurgy Methods 0.000 claims description 2
- RAQDACVRFCEPDA-UHFFFAOYSA-L ferrous carbonate Chemical compound [Fe+2].[O-]C([O-])=O RAQDACVRFCEPDA-UHFFFAOYSA-L 0.000 claims 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 claims 1
- 210000000582 semen Anatomy 0.000 claims 1
- 238000002386 leaching Methods 0.000 description 16
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 8
- 238000006243 chemical reaction Methods 0.000 description 7
- 239000007788 liquid Substances 0.000 description 6
- 239000007789 gas Substances 0.000 description 5
- 238000001556 precipitation Methods 0.000 description 5
- 238000011084 recovery Methods 0.000 description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 5
- 238000003756 stirring Methods 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- 238000003723 Smelting Methods 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 239000000571 coke Substances 0.000 description 2
- 238000007796 conventional method Methods 0.000 description 2
- 238000005260 corrosion Methods 0.000 description 2
- 230000007797 corrosion Effects 0.000 description 2
- 238000003912 environmental pollution Methods 0.000 description 2
- 229910021645 metal ion Inorganic materials 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- JPVYNHNXODAKFH-UHFFFAOYSA-N Cu2+ Chemical compound [Cu+2] JPVYNHNXODAKFH-UHFFFAOYSA-N 0.000 description 1
- PQUCIEFHOVEZAU-UHFFFAOYSA-N Diammonium sulfite Chemical compound [NH4+].[NH4+].[O-]S([O-])=O PQUCIEFHOVEZAU-UHFFFAOYSA-N 0.000 description 1
- 229910000640 Fe alloy Inorganic materials 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 150000001412 amines Chemical class 0.000 description 1
- 235000011114 ammonium hydroxide Nutrition 0.000 description 1
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 1
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 1
- 235000011130 ammonium sulphate Nutrition 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000000975 co-precipitation Methods 0.000 description 1
- 229910001431 copper ion Inorganic materials 0.000 description 1
- 238000005868 electrolysis reaction Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- -1 especially Co Substances 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 238000005065 mining Methods 0.000 description 1
- 230000033116 oxidation-reduction process Effects 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 230000001376 precipitating effect Effects 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000005070 ripening Effects 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- QKMGIVQNFXRKEE-UHFFFAOYSA-L sodium;copper(1+);3-[(n-prop-2-enyl-c-sulfidocarbonimidoyl)amino]benzoate Chemical compound [Na+].[Cu+].[O-]C(=O)C1=CC=CC(NC([S-])=NCC=C)=C1 QKMGIVQNFXRKEE-UHFFFAOYSA-L 0.000 description 1
- 238000000638 solvent extraction Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-L sulfite Chemical compound [O-]S([O-])=O LSNNMFCWUKXFEE-UHFFFAOYSA-L 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Landscapes
- Manufacture And Refinement Of Metals (AREA)
Description
【発明の詳細な説明】 〔産業上の利用分野〕 本発明は深海底マンガンノジュールまたはコバルトク
ラストから、銅,ニッケル,コバルト等の有価金属を回
収する方法に関するものである。TECHNICAL FIELD The present invention relates to a method for recovering valuable metals such as copper, nickel and cobalt from deep sea bottom manganese nodules or cobalt crusts.
マンガンノジュールやコバルトクラストからCu,Ni,Co
などの有価金属を分離回収する方法は種々試みられてお
り、例えばマンガンノジュールからこれらを回収する方
法としては次の方法が知られているが、未だ工業化され
るに到っていない。Manganese nodules and cobalt crusts from Cu, Ni, Co
Various methods for separating and recovering valuable metals have been tried. For example, the following methods are known as methods for recovering these from manganese nodules, but they have not yet been industrialized.
例えば(1)銅イオンの存在下でCOガスによって湿式
還元浸出を行いMnをMnCO3として除き、Cu,Ni,Coを回収
する方法。For example, (1) A method of performing wet reduction leaching with CO gas in the presence of copper ions to remove Mn as MnCO 3 and recover Cu, Ni, and Co.
(2) 245℃、35atmの高温、高圧下で30%硫酸によつ
てCu,Ni,Coを浸出する方法。(2) A method of leaching Cu, Ni, and Co with 30% sulfuric acid under a high pressure of 245 ° C and a high pressure of 35 atm.
(3) 500℃でHClガスを作用させて還元後、水又はHC
l溶液で浸出する方法。(3) After reducing by reacting with HCl gas at 500 ℃, water or HC
l Solution leaching method.
(4) 625〜1000℃でコークス、COガスの存在下で予
備加熱還元し、さらに1425℃でCu,Ni,CoをFe合金とし、
Mn,Feを酸化させスラグとして除去する。次に、石膏と
コークスを加えCu,Ni,Coを硫化物マツトに変え、110
℃、5%H2SO4で浸出する方法。(4) Preheated and reduced in the presence of coke and CO gas at 625 to 1000 ° C, and at 1425 ° C Cu, Ni, Co are made into Fe alloy,
Mn and Fe are oxidized and removed as slag. Next, gypsum and coke were added to change Cu, Ni, and Co to sulfide matte, and 110
Method of leaching with 5% H 2 SO 4 at ℃.
(5) 亜硫酸液で浸出させた後、Fe,Mnを(NH4)2CO3
で沈澱させ濾過分離し、濾液は従来の溶媒抽出や電気分
解の湿式製錬で各金属を分離回収する方法。(5) After leaching with a sulfurous acid solution, Fe and Mn are added to (NH 4 ) 2 CO 3
It is a method of separating and recovering each metal by conventional solvent extraction or hydrometallurgy of electrolysis.
などがあげられる。And so on.
(1)の方法はKennecott Cuprion Processと言われ
常温、常圧反応で環境への影響は少ないがCoの収率は極
めて低い。The method (1) is called Kennecott Cuprion Process, and the reaction at room temperature and pressure has little effect on the environment, but the yield of Co is extremely low.
しかも有害な一酸化炭素を使用するため、環境衛生上
の問題があり、コストの面でも割高となる。Moreover, since harmful carbon monoxide is used, there is a problem in terms of environmental hygiene and the cost is high.
また、(2)の高温・高圧・硫酸浸出法は硫酸のリサ
イクルが困難であるばかりでなく、反応容器の耐蝕性が
問題となる。Further, the high temperature / high pressure / sulfuric acid leaching method (2) not only makes it difficult to recycle sulfuric acid, but also poses a problem of corrosion resistance of the reaction vessel.
さらに(3)の高温下HClガス還元−水又はHClによる
浸出法はほとんどの有価金属成分を浸出させることがで
きるとは言うものの、HClの回収が困難であつて(2)
の方法と同様反応容器の耐蝕性の点でも問題がある。Further, although it can be said that most valuable metal components can be leached by the leaching method of (3) HCl gas reduction under high temperature-water or HCl, it is difficult to recover HCl (2)
Similar to the above method, there is a problem in the corrosion resistance of the reaction vessel.
(4)の乾式製錬・硫酸浸出法は、Mnの回収廃棄を市
況に応じて選択でき、既設のNi製錬設備が活用できる
が、原料の加熱乾燥に莫大なエネルギーを必要とする問
題点がある。In the dry smelting / sulfuric acid leaching method of (4), Mn recovery and disposal can be selected according to market conditions, and existing Ni smelting equipment can be used, but a problem that enormous energy is required to heat and dry the raw material There is.
(5)の亜硫酸浸出法は、常温,常圧で行なえる利点
があるが、濾液中からMnを沈澱,分離,除去する際に、
Coが共沈し、Coの回収率が70%と低くなる問題点があ
る。The sulfurous acid leaching method of (5) has an advantage that it can be carried out at room temperature and atmospheric pressure, but when Mn is precipitated, separated and removed from the filtrate,
There is a problem that Co coprecipitates and the recovery rate of Co is as low as 70%.
文献:溝田忠人,藤井雄二郎,河野好美 日本鉱業会春季大会講演要旨集 P347〜348 1985 このように、従来方法は高温・高圧その他反応条件が
厳しかつたり、エネルギー消費が大であつたりし、かつ
特に共通する欠点は、Coの収率がいずれも50〜70%と低
い点である。References: Tadahito Mizoda, Yujiro Fujii, Yoshimi Kono Proceedings of the Spring Meeting of the Japan Mining Association P347〜348 1985 Thus, the conventional method has high reaction conditions such as high temperature and high pressure and high energy consumption. And, a particularly common drawback is that Co yields are low at 50 to 70%.
本発明の目的はこれらの従来法の問題点をすべて解決
し、低コストでしかも環境汚染を生せず、有価金属を高
収率で回収できる方法を提供するにある。An object of the present invention is to solve all of the problems of the conventional methods, to provide a method of recovering valuable metals in a high yield at a low cost without causing environmental pollution.
本発明は、亜硫酸液を用いて有価成分、特にCo,Cu,Ni
が90%以上の収率で回収できる方法である。The present invention uses a sulfurous acid solution to produce valuable components, particularly Co, Cu, Ni.
Is a method that can be recovered with a yield of 90% or more.
まず粉砕した原鉱は、常温常圧下でH2SO3濃度0.01mol
/以上の亜硫酸溶液中で撹拌する。First, the crushed raw ore has a H 2 SO 3 concentration of 0.01 mol under normal temperature and pressure.
/ Stir in the above sulfite solution.
本発明において亜硫酸液は、H2SO3濃度0.01mol/以
上のものが用いられ、粉砕原鉱はこの中で少くとも1分
以上撹拌される。亜硫酸水と原鉱との重量比は、有価成
分の含有量によって異なるが、MO2+H2SO3→M2++SO4 2-
+H2O(M:金属イオン)の反応に見合う当量以上のH2SO3
であればよい。また亜硫酸水の液量と原鉱重量との比は
機械的に撹拌できればよく特に制約はない。温度は常
温、圧力も常圧で行うことができ、反応装置等に特別の
配慮を払う必要はない。In the present invention, the sulfurous acid solution having a H 2 SO 3 concentration of 0.01 mol / or more is used, and the ground ore is stirred in this for at least 1 minute or more. The weight ratio of sulfite water and raw ore varies depending on the content of valuable components, but MO 2 + H 2 SO 3 → M 2+ + SO 4 2-
+ H 2 O (M: metal ion) equivalent amount of H 2 SO 3
If The ratio between the liquid amount of the sulfite water and the weight of the raw ore is not particularly limited as long as it can be mechanically stirred. The temperature can be room temperature and the pressure can be normal pressure, and it is not necessary to give special consideration to the reaction device or the like.
亜硫酸液で浸出され、遠心分離、フィルダープレスな
どで、固液分離された濾液には、Co,Ni,Cuなどの有価成
分をはじめFe,Mnの金属イオンが含まれる。The filtrate, which has been leached with a sulfite solution, and subjected to solid-liquid separation by centrifugation, field press, etc., contains valuable components such as Co, Ni, Cu and Fe, Mn metal ions.
得た濾液に空気を吹き込みFe2+をFe3+に全部酸化さ
せ、酸性Fe(OH)3の沈澱を精製させ濾過分離させる。Air is blown into the obtained filtrate to completely oxidize Fe 2+ to Fe 3+, and the precipitate of acidic Fe (OH) 3 is purified and separated by filtration.
酸化した酸性領域で沈澱させる理由は、アルカリ側で
のFe(OH)3の沈澱にCo,Ni,Cu等の有価成分が共沈し、
回収率の向上を不可能ならしめるためである。The reason for precipitating in the oxidized acidic region is that valuable components such as Co, Ni, Cu co-precipitate in the precipitation of Fe (OH) 3 on the alkaline side.
This is because it is impossible to improve the recovery rate.
そのためFe2+を酸化しFe3+にして酸性側で沈澱を生成
しなければならない。Therefore, Fe 2+ must be oxidized to Fe 3+ to form a precipitate on the acidic side.
酸化にあっては、O2,O3,空気いずれも酸素を含む気体
を吸込むことによって行える。Oxidation can be performed by sucking a gas containing oxygen into O 2 , O 3 , and air.
次に鉄の除去された濾液に炭酸アンモニウムを加え
る。これは、MnをMnCO3として沈澱させ、Cu,Ni,およびC
oをアンミン錯体とするためである。Ammonium carbonate is then added to the iron-free filtrate. This causes Mn to precipitate as MnCO 3 , causing Cu, Ni, and C
This is because o is an ammine complex.
Cu,NiおよびCoのアンミン錯体をさらに安定化するた
めには、特にCoのアンミン錯体を安定化するためには、
亜硫酸アンモニウム,硫酸アンモニウム,などのアンモ
ニウム塩を加えるか、または、アンモニウム水を加え
る。To further stabilize the ammine complex of Cu, Ni and Co, in particular to stabilize the ammine complex of Co,
Ammonium salts such as ammonium sulfite and ammonium sulfate are added, or ammonium water is added.
上記の添加剤を加え、酸化雰囲気で撹拌を行いMnCO3
を生成、沈澱させ静置し、ほとんどのMn分を濾過分離さ
せる。Add the above additives and stir in an oxidizing atmosphere to remove MnCO 3
Is generated, precipitated, and left to stand, and most of the Mn content is separated by filtration.
酸化雰囲気で撹拌する理由は、Coのアミン錯体である
〔Co(NH4)6〕2+を酸化することによ、より安定な〔C
o(NH4)6〕3+にするためである。The reason for stirring in an oxidizing atmosphere is that by oxidizing [Co (NH 4 ) 6 ] 2+ , which is an amine complex of Co, a more stable [C
This is to make o (NH 4 ) 6 ] 3+ .
安定度定数が〔Co(NH4)6〕3+では、logK=133,〔C
o(NH4)6〕2+では、logK=25.8となり2価の場合は安
定度が低く操作中に分解しやすいことからMnを沈澱させ
る際、安定なコバルトアミン錯体にしておくため、積極
的に〔Co(NH4)6〕3+に酸化させた方がよい。When the stability constant is [Co (NH 4 ) 6 ] 3+ , logK = 133, [C
In case of o (NH 4 ) 6 ] 2+ , logK = 25.8, and in the case of divalent, the stability is low and it is easily decomposed during the operation. It is better to oxidize it to [Co (NH 4 ) 6 ] 3+ .
なお、〔Co(NH4)6〕2+から〔Co(NH4)6〕3+に酸
化するにあたって酸化還元電位を調べると、 〔Co(NH4)6〕3++e-=〔Co(NH4)6〕2+ E0=0.06Vとなり〔Co(NH4)6〕3+の酸化還元電位が極
めて低いことがわかる。In addition, when the redox potential was examined for the oxidation of [Co (NH 4 ) 6 ] 2+ to [Co (NH 4 ) 6 ] 3+ , [Co (NH 4 ) 6 ] 3+ + e − = [Co ( NH 4 ) 6 ] 2+ E 0 = 0.06V, which shows that the oxidation-reduction potential of [Co (NH 4 ) 6 ] 3+ is extremely low.
この電位程度なら容易に酸化することが可能であるの
で、空気吹き込み、あるいは大気中での振とうや強い撹
拌で十分である。さらにこの操作における静置の理由
は、MnからMnCO3の反応が非常に遅いために、十分MnCO3
が沈澱熟成できるようにするためである。Since oxidation can be easily carried out at about this potential, air blowing, shaking in the air, or strong stirring is sufficient. Further reasons stand in this operation, since very slow reaction of MnCO 3 from Mn, sufficient MnCO 3
This is to allow precipitation ripening.
また加温して沈澱生成を促進することが可能である。 It is also possible to heat to accelerate the formation of precipitate.
このようにすることによりFe,Mnを含まずCo,Cu,Miを9
0%以上の回収率で溶液中に回収できる。By doing so, Co, Cu, and Mi are not included in 9
It can be recovered in a solution with a recovery rate of 0% or more.
なお、Mnを分離回収しない場合には、Fe,Mnの同時分
離方法も考えられる。When Mn is not separated and recovered, a method of simultaneously separating Fe and Mn can be considered.
この方法は、原鉱を亜硫酸液で浸出後、浸出液中に溶
解したCo,Cu,Ni,Fe,Mnと浸出残渣を濾過分離し、その濾
液を空気酸化によりFe2+をFe3+に酸化し、その溶液にア
ンモニア水,炭酸アンモニウム等で有価成分を錯体加し
Mn分をMnCO3にし沈澱させ、同時にpHを上げることによ
りFe(OH)3の沈澱とMnCO3の沈澱を一緒に沈澱分離す
る方法である。In this method, after leaching the raw ore with a sulfite solution, Co, Cu, Ni, Fe, Mn dissolved in the leaching solution and the leaching residue are separated by filtration, and the filtrate is oxidized by air to convert Fe 2+ to Fe 3+ . Then, add valuable components to the solution with ammonia water, ammonium carbonate, etc.
This is a method in which the Mn content is converted to MnCO 3 for precipitation, and at the same time, the pH is raised to precipitate and separate the precipitation of Fe (OH) 3 and the precipitation of MnCO 3 .
また、亜硫酸液浸出残渣、FeおよびMnを有価成分と一
括分離する方法、つまり亜硫酸液浸出残渣を除去せず有
価成分を含む溶液に含まれているFe2+をFe3+とし、次に
Mn分をMnCO3に生成、同時にpHを上げてFe(OH)3を沈
澱させて有価成分と分離を行うと、沈澱物に有価成分が
Co19.3%,Cu9.8%、Ni5.8%と残るが、有価成分を溶液
中に回収することができる。Further, a method of collectively separating the sulfurous acid solution leaching residue, Fe and Mn from the valuable component, that is, Fe 2+ contained in the solution containing the valuable component without removing the sulfite liquid leaching residue is set to Fe 3+, and then
When Mn is generated in MnCO 3 , pH is raised and Fe (OH) 3 is precipitated at the same time to separate the valuable component from the valuable component.
Co19.3%, Cu9.8% and Ni5.8% remain, but valuable components can be recovered in the solution.
MnおよびFeの原鉱品位が高いので、上記のいずれの方
法によってもCo,CuおよびNiの貴液中には、Cu,Niと同程
度のMnと微量のFeが残る。Since the raw ore grades of Mn and Fe are high, Mn and a trace amount of Fe, which are about the same as Cu and Ni, remain in the precious liquids of Co, Cu and Ni by any of the above methods.
これらをさらに分離する方法としてこの貴液中にMnCO
3との共沈効果の期待できる共沈剤を添加することも可
能である。As a method for further separating these, MnCO
It is also possible to add a coprecipitating agent that is expected to have a coprecipitation effect with 3 .
この場合の共沈剤はCaCl2である。The coprecipitant in this case is CaCl 2 .
Fe,Mnと有価成分の分離は、次の反応に見合うだけの
(NH4)2CO3とCaCl2を添加し、1時間以上沈澱熟成させ
濾過分離する。To separate Fe, Mn and valuable components, (NH 4 ) 2 CO 3 and CaCl 2 are added in an amount corresponding to the next reaction, and the mixture is precipitated and aged for 1 hour or more, and separated by filtration.
Mn2++CaCl2+2(NH4)2CO3→MnCO3↑+CaCO3↓ +2NH4Cl+2NH4 +Fe,Mnは、CaCO3の沈澱に効率よく共沈
し、貴液中のFe,Mn濃度を著しく低下せしめる。Mn 2+ + CaCl 2 +2 (NH 4 ) 2 CO 3 → MnCO 3 ↑ + CaCO 3 ↓ + 2NH 4 Cl + 2NH 4 + Fe, Mn co-precipitate CaCO 3 efficiently and the concentration of Fe and Mn in the noble liquid Remarkably lower.
以上のように、Fe,Mnを同時に分離する方法もある
が、Fe,Mnをそれぞれ個別的に有効に利用しようとする
場合には適さない。As described above, there is a method of separating Fe and Mn at the same time, but it is not suitable when each of Fe and Mn is to be effectively utilized individually.
表1に示す化学成分を有するマンガンノジュール1gに
H2SO3濃度0.2mol/の亜硫酸水を100ml入れ、25℃で1
時間振とうして有価成分の浸出を行なった。1g of manganese nodule with the chemical composition shown in Table 1
Add 100 ml of H 2 SO 3 0.2 mol / sulfite water at 25 ℃
The valuable component was leached by shaking for time.
浸出後、遠心分離機で固液分離を行なった。濾液には
Cu,Ni,Co,Mn,Feイオンが存在する。残渣には原鉱に含ま
れるFe分の26.7%が残った。After leaching, solid-liquid separation was performed with a centrifuge. In the filtrate
Cu, Ni, Co, Mn, Fe ions are present. 26.7% of Fe contained in the original ore remained in the residue.
次に濾液に空気を500ml/min、2.5時間吹き込み酸化さ
せた。空気酸化させた濾液に濃度0.5mol/のNa2CO33ml
を入れ、pHを4.04として1時間空気酸化させた。Next, air was blown into the filtrate at 500 ml / min for 2.5 hours for oxidation. 3 ml of Na 2 CO 3 with a concentration of 0.5 mol / in the air-oxidized filtrate
Was added and the pH was adjusted to 4.04 and air oxidation was carried out for 1 hour.
これにより、FeはFe(OH)3として沈澱した。このFe
(OH)3沈澱物を含む液を遠心分離機にかけ、この水酸
化沈澱物を分離した。This caused Fe to precipitate as Fe (OH) 3 . This Fe
The solution containing the (OH) 3 precipitate was centrifuged to separate the hydroxylated precipitate.
除鉄した濾液に、(NH4)2CO3を5g入れ、濃度28%のN
H4OH15mlを入れた。Add 5 g of (NH 4 ) 2 CO 3 to the iron-free filtrate, and add 28% N
15 ml of H 4 OH was added.
さらに、(NH4)2SO4を5grを濾液に入れ、100r.p.m1.
5時間で振とうした。Further, 5 gr of (NH 4 ) 2 SO 4 was added to the filtrate, and 100 r.p.m1.
Shake for 5 hours.
振とう後溶液は2日間静置させ、Mnを沈澱分離した。
最終濾液で、Cu,Ni,Coの回収率は、それぞれ94.0%,94.
2%,94.4%であった。After shaking, the solution was allowed to stand for 2 days to precipitate and separate Mn.
In the final filtrate, the recovery rates of Cu, Ni and Co were 94.0% and 94.
It was 2% and 94.4%.
結果をまとめて表2に示す。 The results are summarized in Table 2.
〔発明の効果〕 亜硫酸水浸出によって常温、常圧下で浸出できるので
設備も簡単であり、環境汚染の問題もなく、実施上極め
て有利であるのみならず、有価金属特にCo,Ni,Cu等を90
%以上という高い収率でしかもMn,Feの存在の少ない状
態で分離回収することができる。 (Effect of the invention) Room temperature by sulphite leaching, the facility is simple because it can be leached under normal pressure, there is no problem of environmental pollution, not only extremely advantageous in practice, valuable metals, especially Co, Ni, Cu, etc. 90
It can be separated and recovered with a high yield of at least%, and in a state in which Mn and Fe are little present.
Claims (1)
ストの原鉱から有価成分を分離するにあたり、マンガン
ノジュールまたは、コバルトクラストの原鉱をH2SO3濃
度0.01mol/以上の亜硫酸液中で有価成分を溶出せしめ
溶解残渣と溶出液を濾過分離し、次いでその溶出液に酸
化性気体を吹き込み、Fe2+をFe3+に酸化させ、酸性領域
内でFe(OH)3の水酸化物を沈澱させ、鉄分を分離さ
せ、鉄分を除去した濾液に炭酸アンモニウムを加え、さ
らに、アンモニウム塩、またはアンモニア水を加えて、
空気酸化後、静置し、マンガンをMnCO3の沈澱物として
分離し、銅,ニッケル,コバルト等の有価成分を湿式製
錬用に濾液中に残すことを特徴とするマンガンノジュー
ルまたはコバルトクラストから有価金属を分離回収する
方法。1. When separating a valuable component from a manganese nodule or cobalt crust raw ore, the valuable component is eluted from a manganese nodule or cobalt crust raw ore in a sulfurous acid solution having a H 2 SO 3 concentration of 0.01 mol / or more. The semen solution residue and the eluate are separated by filtration, and then the eluate is blown with an oxidizing gas to oxidize Fe 2+ to Fe 3+ to precipitate Fe (OH) 3 hydroxide in the acidic region, Iron carbonate was separated, ammonium carbonate was added to the filtrate from which iron was removed, and further ammonium salt or aqueous ammonia was added,
After air oxidation, the mixture was left to stand, manganese was separated as MnCO 3 precipitate, and valuable components such as copper, nickel, and cobalt were left in the filtrate for hydrometallurgy. A method of separating and recovering metals.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP22950986A JPH086150B2 (en) | 1986-09-30 | 1986-09-30 | Method for separating and recovering valuable metals from manganese nodules or cobalt crusts |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP22950986A JPH086150B2 (en) | 1986-09-30 | 1986-09-30 | Method for separating and recovering valuable metals from manganese nodules or cobalt crusts |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6386824A JPS6386824A (en) | 1988-04-18 |
| JPH086150B2 true JPH086150B2 (en) | 1996-01-24 |
Family
ID=16893289
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP22950986A Expired - Fee Related JPH086150B2 (en) | 1986-09-30 | 1986-09-30 | Method for separating and recovering valuable metals from manganese nodules or cobalt crusts |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH086150B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR101514837B1 (en) * | 2014-11-06 | 2015-04-28 | 한국지질자원연구원 | The preparation method of sulfides using oxide flux from deep ocean manganese nodules |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| MX2010000141A (en) * | 2007-07-13 | 2010-03-15 | Metaleach Ltd | Method for ammoniacal leaching. |
| FR2948946B1 (en) * | 2009-08-07 | 2015-08-07 | Metaleach Ltd | PROCESS FOR LEACHING COBALT FROM COBALT OXIDE ORES |
| US12215407B2 (en) | 2019-08-09 | 2025-02-04 | Umicore | Process for the recovery of metals from oxidic ores |
-
1986
- 1986-09-30 JP JP22950986A patent/JPH086150B2/en not_active Expired - Fee Related
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR101514837B1 (en) * | 2014-11-06 | 2015-04-28 | 한국지질자원연구원 | The preparation method of sulfides using oxide flux from deep ocean manganese nodules |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6386824A (en) | 1988-04-18 |
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