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JPS6366370B2 - - Google Patents
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JPS6366370B2 - - Google Patents

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Publication number
JPS6366370B2
JPS6366370B2 JP16264582A JP16264582A JPS6366370B2 JP S6366370 B2 JPS6366370 B2 JP S6366370B2 JP 16264582 A JP16264582 A JP 16264582A JP 16264582 A JP16264582 A JP 16264582A JP S6366370 B2 JPS6366370 B2 JP S6366370B2
Authority
JP
Japan
Prior art keywords
acid
solution
leaching
nickel
solid
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
Application number
JP16264582A
Other languages
Japanese (ja)
Other versions
JPS5953638A (en
Inventor
Hiroto Matsumoto
Tadashige Shiga
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.)
Nippon Steel Nisshin Co Ltd
Original Assignee
Nisshin Steel Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Nisshin Steel Co Ltd filed Critical Nisshin Steel Co Ltd
Priority to JP57162645A priority Critical patent/JPS5953638A/en
Publication of JPS5953638A publication Critical patent/JPS5953638A/en
Publication of JPS6366370B2 publication Critical patent/JPS6366370B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Manufacture And Refinement Of Metals (AREA)

Description

【発明の詳现な説明】[Detailed description of the invention]

本発明は、Ni−Sn系廃觊媒から、特にNiをス
テンレス鋌のNi源ずしお有効利甚するために、
SnおよびNiを分離回収する方法に関する。 䞀般にステンレス鋌の補造におけるニツケル源
ずしおは、プロニツケル、金属ニツケル、ニツ
ケル屑および酞化ニツケルが、䜿いわけられおい
る。䜿甚枈のNi含有廃觊媒をそのたた盎接ステ
ンレス鋌の補鋌原料ずしお䜿甚する堎合、圓該廃
觊媒䞭に含たれおいるこずがあるFe、Cr、Ti、
Mo、Mg、CaおよびCuならびに担持䜓ずしおの
Al2O3およびSiO2の存圚は特に問題ずならない
が、Snの存圚は奜たしくない。補鋌原料䞭のSn
は粟錬によ぀おもほずんど陀去されるこずがなく
鋌䞭に残存し、倧型鋌塊においおは著しく偏析し
熱間加工性を害する䞊、鋌の靭性をそこなう傟向
がある。したが぀おNi−Sn系廃觊媒をステンレ
ス鋌補造におけるNi源ずしお有効に利甚するた
めには、圓該廃觊媒からNiおよびSn分を効果的
に分離回収する凊理法の確立が望たれる。 特公昭56−47254号公報は、廃觊媒から有䟡金
属を分離回収する方法を開瀺する。この特蚱公報
の方法では、觊媒を酞化焙焌しおを陀去し、さ
らにアルカリ焙焌、氎抜出および過を行ない
Mo、を、さらには高磁力磁遞機によりNi、Co
を、たた担持䜓剀であるAlをも回収しおいるが、
Snに぀いおの蚀及がない。 したが぀お本発明の目的は、Ni−Sn系廃觊媒
からNiおよびSn実質的に完党に分離回収する方
法を提䟛するこずである。 本発明によれば、Ni−Sn系廃觊媒を非酞化性
の鉱酞で枩浞し、埗られた液を脱酞埌PH1.0〜2.0
で逊生するこずにより、Sn分をメタスズ酞ずし
お遞択的に分離できるこずがわか぀た。Sn分を
分離埌、Ni分は氎酞化ニツケルずしお分離でき、
そしおそれらのメタスズ酞および氎酞化ニツケル
は焙焌によりそれぞれ酞化スズおよび酞化ニツケ
ルに、所望ならさらにそれらの酞化スズおよび酞
化ニツケルは還元によりそれぞれ金属スズおよび
金属ニツケルに倉換される。 かくしおセラミツクス担䜓䞊にNiおよびSnを
担持させおなるNi−Sn系廃觊媒からNiおよびSn
を分離回収する本発明方法は、次の諞工皋 (a) 前蚘廃觊媒を非酞化性の鉱酞で浞出するこず
により抜出されたNi分およびSn分を溶解含有
する酞液を埗る工皋、 (b) 工皋(a)の酞液から固圢分を陀去埌酞分を陀去
する工皋、 (c) 工皋(b)の酞分を陀去した溶液をPHを1.0〜2.0
にするこずによりメタスズ酞を析出させる工
皋、 (d) 工皋(c)のメタスズ酞を懞濁含有する液を固−
液分離する工皋、 (e) 工皋(d)で埗た固圢分を焙焌しお酞化スズを回
収する工皋、 (f) 工皋(d)で埗た液をアルカリで䞭和するこずに
より氎酞化ニツケルを析出させる工皋、 (g) 工皋(f)の氎酞化ニツケルを懞濁含有する液を
固−液分離する工皋、および (h) 工皋(g)で埗た固圢分を焙焌しお酞化ニツケル
を回収する工皋 からなり、そしお所望なら、 (i) 工皋(e)で回収した酞化スズを還元しお金属ス
ズを回収する工皋およびたたは (j) 工皋(h)で回収した酞化ニツケルを還元しお金
属ニツケルを回収する工皋 をさらに含むこずができる。 添付の第図は、本発明方法の奜たしい実斜態
様を説明するためのフロヌシヌトである。 本発明方法により凊理される出発廃觊媒は、ア
ルミナ、アルミナ・シリカなどのセラミツクス担
䜓䞊にNi、Snおよびその他の金属が担持されお
なるNi−Sn系廃觊媒であ぀お、その化孊組成は
たずえば衚に瀺す劂きものであるこずができ
る。
The present invention aims to effectively utilize Ni from Ni-Sn-based waste catalysts, especially as a Ni source for stainless steel.
This invention relates to a method for separating and recovering Sn and Ni. In general, nickel sources used in the production of stainless steel include ferronickel, metallic nickel, nickel scrap, and nickel oxide. When used Ni-containing waste catalyst is directly used as raw material for making stainless steel, Fe, Cr, Ti, and
Mo, Mg, Ca and Cu and as supports
Although the presence of Al 2 O 3 and SiO 2 is not particularly problematic, the presence of Sn is not desirable. Sn in steelmaking raw materials
They are hardly removed even during refining and remain in the steel, and they segregate significantly in large steel ingots, impairing hot workability and tending to impair the toughness of the steel. Therefore, in order to effectively utilize the Ni-Sn-based waste catalyst as a Ni source in stainless steel production, it is desired to establish a processing method for effectively separating and recovering Ni and Sn from the waste catalyst. Japanese Patent Publication No. 56-47254 discloses a method for separating and recovering valuable metals from waste catalysts. In the method of this patent publication, the catalyst is oxidized and roasted to remove S, and then subjected to alkaline roasting, water extraction, and filtration.
Mo, V, and even Ni, Co using a high-magnetic separator
, and Al, which is a carrier agent, is also recovered.
There is no mention of Sn. Therefore, an object of the present invention is to provide a method for substantially completely separating and recovering Ni and Sn from a Ni-Sn-based waste catalyst. According to the present invention, a Ni-Sn-based waste catalyst is digested with a non-oxidizing mineral acid, and the resulting liquid is deoxidized to a pH of 1.0 to 2.0.
It was found that the Sn content could be selectively separated as metastannic acid by curing with water. After separating the Sn component, the Ni component can be separated as nickel hydroxide.
The metastannic acid and nickel hydroxide are then converted to tin oxide and nickel oxide, respectively, by roasting, and if desired, the tin oxide and nickel oxide are further converted to metallic tin and metallic nickel, respectively, by reduction. In this way, Ni and Sn can be extracted from the Ni-Sn-based waste catalyst, which is made by supporting Ni and Sn on a ceramic carrier.
The method of the present invention for separating and recovering the catalyst includes the following steps (a) obtaining an acid solution containing dissolved Ni and Sn extracted by leaching the waste catalyst with a non-oxidizing mineral acid; b) A step of removing the acid content after removing the solid content from the acid solution in step (a); (c) A step of removing the acid content from the acid solution in step (b) to a pH of 1.0 to 2.0.
(d) solidifying the liquid containing metastannic acid suspended in step (c);
(e) Roasting the solid content obtained in step (d) to recover tin oxide; (f) Neutralizing the liquid obtained in step (d) with an alkali to produce hydroxide. a step of precipitating nickel; (g) a step of solid-liquid separation of the liquid containing suspended nickel hydroxide in step (f); and (h) a step of roasting and oxidizing the solid content obtained in step (g). and, if desired, (i) reducing the tin oxide recovered in step (e) to recover tin metal; and/or (j) reducing the nickel oxide recovered in step (h). The method may further include a step of reducing and recovering the nickel metal. The attached FIG. 1 is a flow sheet for explaining a preferred embodiment of the method of the present invention. The starting waste catalyst treated by the method of the present invention is a Ni-Sn-based waste catalyst in which Ni, Sn, and other metals are supported on a ceramic carrier such as alumina or alumina-silica, and its chemical composition is, for example, It can be as shown in Table 1.

【衚】 かような廃觊媒は、たずえば石油粟補工業にお
ける脱氎玠化法などから埗られる。 第図を参照するに、出発廃觊媒は、ふるいわ
け、酞化焙焌および粉砕からなる予備凊理
に付すのが奜たしい。すなわち、出発廃觊媒は、
ふるいわけによ぀お担持䜓セラミツクスが可及
的に陀去された埌、酞化焙焌に付される。この
酞化焙焌は、廃觊媒に付着しおいる油分その他
の有機物を焌华陀去するための工皋であ぀お、焙
焌枩床は油分およびその他の有機物を灰化するに
充分な枩床、たずえば玄200℃〜800℃の枩床であ
るこずができる。粉砕工皋においおは、埌の酞
枩浞工皋における金属分ず酞ずの固−液接觊を
充分ならしめるために、廃觊媒をたずえば100〜
150メツシナ通過皋床の粒床にたで埮粉砕する。 本発明方法では、出発廃觊媒を、奜たしくは前
蚘の予備凊理に付した埌、非酞化性の鉱酞で浞出
するこずにより抜出されたNi分およびSn分を溶
解含有する酞液を埗る。浞出甚酞ずしおは、塩
酞、皀硫酞および燐酞のような非酞性の鉱酞が適
切である。硝酞のような酞化性の酞を甚いるず、
Snの䞀郚が加氎分解するため、Snの抜出率が䜎
䞋する。NiおよびSnを実質的に完党に抜出する
ためには塩酞が最も奜たしいこずがわか぀た。こ
の浞出は、しかるべき撹拌手段ず加熱手段ずを
備えた、FRP内匵を斜した鋌補の浞出槜に浞出
酞および予備凊理を斜した廃觊媒を䟛絊しお加
熱䞋で撹拌混合するこずにより行なうのが䟿利で
ある。この堎合、浞出槜の容積は、凊理される廃
觊媒量および凊理時間によ぀お定たる。別法ずし
おは、廃觊媒を述填した塔に昇枩された浞出酞を
反埩流通させるこずによ぀お浞出を行なうこずも
できる。浞出には、觊媒䞭に含たれるNiおよび
Snの党量を溶解するのに必芁な化孊量論量の玄
〜倍の量を䜿甚するのがよい。浞出酞の䜿甚
量が過小であればNiおよびSnの抜出率が䜎䞋す
るし、たた浞出酞の䜿甚量が過倧であれば埌の酞
分陀去工皋における負荷が過倧になる。䜿甚する
浞出酞の濃床は、塩酞の堎合は塩酞察氎、又
は塩酞察氎、皀硫酞の堎合は硫酞察氎又
は硫酞察氎ずするのが奜たしい。浞出濃床は
65℃〜100℃、特に75℃〜90℃ずするのが奜たし
い。本明现曞に蚘茉する奜たしい諞条件䞋で浞出
を行なえば、出発廃觊媒䞭のNiの略々100およ
びSnの98.8以䞊を抜出できる。 酞浞出で埗たNi分およびSn分を溶解含有する
酞液を固−液分離たずえば過に付し、酞に䞍
溶なアルミナおよびシリカなどからなる固圢分
を陀去する。埗られる溶液の組成の䞀䟋をあげ
れば、たずえば、衚に瀺した詊料を、詊料
äž­NiおよびSnの党量を溶解するのに必芁な化孊
量論量の倍に盞圓する量モルの塩酞を甚
いお凊理しお埗た溶液の組成、Ni22.1、
Sn4.15、遊離塩酞1.9モルである。 本発明方法の次の工皋では、このようにしお埗
たNi分およびSn分を溶解含有し、か぀遊離の酞
分を含む溶液から、遊離の酞分を陀去する。この
酞分陀去工皋は、むオン亀換膜を甚いる拡散透
析法により行なうのが奜郜合である。揮発性の
酞、たずえば塩酞、を浞出酞ずしお甚いた堎合に
は、加熱蒞留法によ぀お酞分を陀去するこずもで
きる。酞分陀去工皋から回収された酞は、浞出
酞ずしお再䜿甚する。 次の工皋は、前蚘の酞分を陀去した溶液をPHを
〜にするこずによりメタスズ酞を析出させる
工皋である。PH調節は、氎で垌釈するこずに
より行なうのが䟿利である。メタスズ酞の析出の
ためには、1.0以䞊のPHが必芁であるが、PHが2.0
を実質的に越えるず、他の金属の氎酞化物が析出
しおくる䞍郜合がある。PH調節にあたり、メタス
ズ酞の析出を容易ならしめるためには、溶液をた
ずえば40℃〜50℃の枩床に加枩するのが奜たし
く、たた酞化剀の添加およびたたは誘発剀
の添加が奜たしい。酞化剀ずしおは、た
ずえば硝酞、塩玠酞塩又は過酞化氎玠があり、溶
液䞭に存圚するSn30〜50あたり、〜
の量でかような酞化剀を添加するのがよい。酞
玠および酞玠含有ガスすなわち空気も酞化剀
ずしお䜿甚でき、たずえば溶液あたり、空気
0.2〜0.3Nminの゚ダヌレヌシペンを行なう
のもよい。メタスズ酞栞の生成誘発剀ずしお
は、スズ塩たずえば塩化第スズ、塩化第錫、
硫酞スズなどをSn30〜50あたり0.3〜0.5
の量で添加できる。 析出したメタスズ酞を懞濁含有する液は、固−
液分離に付す。固−液分離は、過、遠心分
離その他の適切な技法により行なえる。 埗られた固圢分メタスズ酞は、これを
焙焌しお酞化スズを回収する。焙焌枩床
は玄800〜1000℃ずするこずができる。 固−液分離によ぀お埗られた溶液は、
たずえば前蚘の䟋では、21.66のNi分ずト
レヌスのズズ分を溶解含有し、そのPHは1.2〜1.4
であ぀た。 この液は、アルカリで䞭和し、氎
酞化ニツケルを析出させる。アルカリずしお
は、CaOH2、Na2CO3、NaOHその他を䜿甚で
きる。 氎酞化ニツケルを懞濁含有する液は、過その
他の固−液分離に付し、埗られた固圢分
氎酞化ニツケルはこれを焙焌しお酞化ニ
ツケルを回収する。焙焌枩床は800℃〜1000
℃ずするこずができる。䞀方、固−液分離か
ら埗られた液は、䞭和甚アルカリ液の調
補に䜿甚できる。 焙焌によ぀お埗られた酞化スズは、そ
のたた粟補するこずなく化孊詊薬ずしお䜿甚でき
るし、たた所望なら、これを垞法により、たずえ
ば500℃〜800℃の枩床においおH3CO、などで
還元するこずにより、金属スズずするこ
ずもできる。 焙焌によ぀お埗られた酞化ニツケル
は、盎接ステンレス鋌補鋌のNi源ずしお䜿甚で
きるし、たた所望なら、これを垞法により、たず
えばH2気流䞭では650℃〜700℃の枩床においお
たた、朚炭の堎合は1200〜1250℃で還元する
こずにより、金属ニツケルずするこずもでき
る。 このようにしお、本発明方法によれば、Ni−
Sn系廃觊媒から、有䟡金属であるNiおよびSnを
効果的に分離し、高収率で回収するこずができ
る。 次に具䜓䟋をあげ本発明方法をさらに説明す
る。 実斜䟋  衚に瀺したNo.の組成の廃觊媒をテむラ粒床
100〜150メツシナに粉砕し、この廃觊媒䞭のNi
およびSnの党量を溶解するのに必芁な化孊量論
量の倍に盞圓する量すなわちモルの塩酞濃
床14.6を甚いお、80℃の枩床で時間撹拌し
ながら枩浞し、固圢分を別埌Ni35.24、
Sn2.37および遊離塩酞1.8モルを含む酞
液を埗た。この酞液を、1.0m2hrの流速で流
す40℃の氎ずむオン亀換膜を介しお同じく1.0
m2hrの流速で逆方向に流しお透析するこずに
より、脱酞し、脱酞液ず回収酞ずを埗た。埗られ
た脱酞液の組成はNi33.62、Sn22.4
、遊離酞塩0.15モルであ぀た。たた回収酞
の組成は、Ni1.62、Sn0.13、遊
離塩酞2.03モルであ぀た。次いでこの脱酞液を
倍量の氎で垌釈しPHを1.2〜1.4ずし、メタスズ酞
の析出を完党ならしめるために玄45℃に加枩しか
぀塩化第スズ結晶2.5を添加しお逊生す
るこずにより、コロむド状のβメタスズ酞を析出
させ、そしお過により固−液分離した。 沈殿を玄900℃で焙焌し実質䞊玔粋な酞化スズ
を回収した。回収率は玄95であ぀た。未回収の
玄は、むオン亀換時に回収酞偎に移行した
Sn分であり、このSn分は回収酞ず共に浞出甚酞
ずしお埪環されるから、系倖に持ち去られるこず
はない。 䞀方液にはCaOH2氎溶液を加えお䞭和し、
氎酞化ニツケルを析出させ、取し、そしお玄
1000℃で焙焌しお酞化ニツケルを回収した。回収
率は95であ぀た。 埗られた酞化スズず玄700℃の枩床で氎玠ガス
で還元したずころ98.0の倉換率で金属スズが埗
られた。たた、埗られた酞化ニツケルを玄700℃
の枩床においお氎玠ガスで還元したずころ、略々
100の倉換率で金属ニツケルが埗られた。 脱酞を加熱蒞留法により行な぀た以倖は前蚘の
操䜜を回埩したずころ、略々同様な結果が埗られ
た。
[Table] Such waste catalysts are obtained, for example, from dehydrogenation processes in the petroleum refining industry. Referring to FIG. 1, the starting spent catalyst is preferably subjected to a pretreatment consisting of sieving 1, oxidative roasting 2 and grinding 3. That is, the starting spent catalyst is
After the carrier ceramic is removed as much as possible by sieving 1, it is subjected to oxidative roasting 2. This oxidation roasting 2 is a process for incinerating and removing oil and other organic substances adhering to the waste catalyst, and the roasting temperature is a temperature sufficient to ash the oil and other organic substances, for example, about 200℃. The temperature can be from ℃ to 800℃. In the pulverization step 3, the waste catalyst is, for example,
Pulverize to a particle size that can pass through a 150 mesh mill. In the method of the present invention, the starting waste catalyst is preferably subjected to the above-mentioned pretreatment and then leached with a non-oxidizing mineral acid to obtain an acid solution containing the extracted Ni and Sn dissolved therein. Suitable leaching acids 4 are non-acidic mineral acids such as hydrochloric acid, dilute sulfuric acid and phosphoric acid. When using an oxidizing acid such as nitric acid,
Since a portion of Sn is hydrolyzed, the extraction rate of Sn decreases. Hydrochloric acid was found to be most preferred for substantially complete extraction of Ni and Sn. In this leaching 5, the leaching acid 4 and the pretreated waste catalyst are fed into a steel leaching tank lined with FRP and equipped with appropriate stirring means and heating means, and the leaching acid 4 and the pretreated waste catalyst are stirred and mixed under heating. It is convenient to do this by In this case, the volume of the leaching tank is determined by the amount of waste catalyst to be treated and the treatment time. Alternatively, leaching can be carried out by repeatedly passing heated leaching acid through a column filled with spent catalyst. Leaching involves Ni and
It is preferable to use an amount approximately 2 to 7 times the stoichiometric amount required to dissolve the entire amount of Sn. If the amount of leaching acid used is too small, the extraction rate of Ni and Sn will decrease, and if the amount of leaching acid used is too large, the load in the subsequent acid removal step will become excessive. The concentration of the leaching acid used is preferably 1 part hydrochloric acid to 2 parts water, or 1 part hydrochloric acid to 3 parts water, and in the case of dilute sulfuric acid, 1 part sulfuric acid to 4 parts water or 1 part sulfuric acid to 6 parts water. The leaching concentration is
The temperature is preferably 65°C to 100°C, particularly 75°C to 90°C. When leaching is performed under the preferred conditions described herein, approximately 100% of the Ni and 98.8% or more of the Sn in the starting spent catalyst can be extracted. The acid solution containing dissolved Ni and Sn obtained by acid leaching is subjected to solid-liquid separation 6, for example, to remove the solid content 7, which consists of acid-insoluble alumina and silica.
remove. To give an example of the composition of the resulting solution 8, (for example, sample 4 shown in Table 1 is mixed with an amount equivalent to four times the stoichiometric amount required to dissolve the entire amount of Ni and Sn in the sample) ( Composition of the solution obtained by treatment with 4 mol) of hydrochloric acid), Ni; 22.1 g/,
Sn: 4.15 g/, free hydrochloric acid: 1.9 mol. In the next step of the method of the present invention, the free acid content is removed from the solution obtained in this way that contains the dissolved Ni and Sn content and also contains the free acid content. This acid removal step 9 is conveniently carried out by diffusion dialysis using an ion exchange membrane. When a volatile acid, such as hydrochloric acid, is used as the leaching acid, the acid content can also be removed by thermal distillation. The acid recovered from the acid removal step 9 is reused as leaching acid 4. The next step is Step 10, in which metastannic acid is precipitated by adjusting the pH of the acid-free solution to 1 to 2. PH adjustment is conveniently carried out by dilution with water. For the precipitation of metastannic acid, a pH of 1.0 or higher is required, but a pH of 2.0 is required.
If it substantially exceeds this, there is a problem that hydroxides of other metals will precipitate. In adjusting the pH, in order to facilitate the precipitation of metastannic acid, it is preferable to heat the solution to a temperature of, for example, 40°C to 50°C, and it is also preferable to add the oxidizing agent 11 and/or the inducing agent 12. . Examples of the oxidizing agent 11 include nitric acid, chlorate or hydrogen peroxide, and the amount of oxidizing agent 11 is 2 to 5 per 30 to 50 g of Sn present in the solution.
It is preferable to add such an oxidizing agent in an amount of .g. Oxygen and oxygen-containing gases, i.e. air, are also oxidizing agents 11
For example, per solution, air
It is also good to perform air ration at 0.2 to 0.3 N/min. As the metastannic acid nucleus generation inducing agent 12, tin salts such as stannous chloride, stannic chloride,
Sn30~50g/0.3~0.5g of tin sulfate etc.
It can be added in an amount of The liquid containing precipitated metastannic acid in suspension is solid.
Subjected to liquid separation 13. Solid-liquid separation can be performed by filtration, centrifugation or other suitable techniques. The obtained solid content 14 (metastannic acid) is roasted 15 to recover tin oxide 16. The roasting temperature can be about 800-1000°C. The solution 17 obtained by solid-liquid separation 13 is
For example, in the above example, it contains 21.66g/Ni and trace trace, and its pH is 1.2 to 1.4.
It was hot. This liquid 17 is neutralized 18 with an alkali 19 to precipitate nickel hydroxide. As the alkali 19, Ca(OH) 2 , Na 2 CO 3 , NaOH and others can be used. The liquid containing nickel hydroxide in suspension is subjected to filtration or other solid-liquid separation 20, resulting in a solid content of 21
(Nickel hydroxide) is roasted 15 to recover nickel oxide 22. Roasting temperature is 800℃~1000℃
It can be ℃. On the other hand, the liquid 23 obtained from the solid-liquid separation 20 can be used to prepare the alkaline solution 19 for neutralization. The tin oxide 16 obtained by roasting 15 can be used as a chemical reagent as it is without purification, and if desired, it can be treated with H 3 CO, C by a conventional method at a temperature of, for example, 500°C to 800°C. Metal tin 25 can also be obtained by reducing 24 with, for example, the following. Nickel oxide 22 obtained by roasting 15
can be used directly as a source of Ni in stainless steel production, or if desired, it can be reduced by conventional methods, e.g. 24, it is also possible to use metal nickel 26. In this way, according to the method of the present invention, Ni-
Ni and Sn, which are valuable metals, can be effectively separated from Sn-based waste catalyst and recovered in high yield. Next, the method of the present invention will be further explained by giving specific examples. Example 1 The spent catalyst with the composition No. 3 shown in Table 1 was
The Ni in this waste catalyst is crushed into 100 to 150 mesh pieces.
and Digested with stirring at 80°C for 2 hours using an amount equivalent to 4 times the stoichiometric amount required to dissolve the entire amount of Sn, that is, 4 mol of hydrochloric acid (concentration 14.6%), and solidified. After separating Ni; 35.24g/,
An acid solution containing 2.37 g of Sn and 1.8 mol of free hydrochloric acid was obtained. This acid solution was passed through an ion exchange membrane with 40°C water flowing at a flow rate of 1.0/m 2 hr.
By dialysis by flowing in the opposite direction at a flow rate of /m 2 hr, deacidification was performed, and a deacidified solution and recovered acid were obtained. The composition of the obtained deoxidizing solution was Ni: 33.62 g/, Sn: 22.4
g/, 0.15 mol of free acid salt. The composition of the recovered acid was 1.62 g/Ni, 0.13 g/Sn, and 2.03 mol of free hydrochloric acid. Next, add this deoxidizing solution to 2
The colloid was diluted with twice the amount of water to bring the pH to 1.2 to 1.4, heated to about 45°C to complete the precipitation of metastannic acid, and cured by adding 2.5 g of stannous chloride crystals. β-metastannic acid was precipitated and solid-liquid separated by filtration. The precipitate was roasted at approximately 900°C to recover substantially pure tin oxide. The recovery rate was approximately 95%. Approximately 5% of the unrecovered material was transferred to the recovered acid side during ion exchange.
This Sn content is circulated as a leaching acid together with the recovered acid, so it is not carried away from the system. One solution was neutralized by adding Ca(OH) 2 aqueous solution,
Nickel hydroxide is precipitated, removed, and about
Nickel oxide was recovered by roasting at 1000℃. The recovery rate was 95%. When the obtained tin oxide was reduced with hydrogen gas at a temperature of approximately 700°C, metallic tin was obtained with a conversion rate of 98.0%. In addition, the obtained nickel oxide was heated to about 700°C.
When reduced with hydrogen gas at a temperature of approximately
Metallic nickel was obtained with 100% conversion. When the above procedure was repeated except that deoxidation was carried out by a heated distillation method, substantially the same results were obtained.

【図面の簡単な説明】[Brief explanation of drawings]

第図は本発明方法の奜たしい実斜態様を説明
するためのフロヌシヌトである。 図䞭  ふるいわけ、  焙焌、  粉
砕、  浞出酞、  浞出、  固−液分
離、  䞍溶解分、  溶液、  酞分陀
去、  メタスズ酞逊生、  酞化剀、
  誘発剀、  固−液分離、  
メタスズ酞、  焙焌、  酞化スズ、
  溶液、  䞭和、  アルカリ
䞭和剀、  固−液分離、  氎酞化ニ
ツケル、  酞化ニツケル、  溶液、
  還元、  金属スズ、  金属
ニツケル。
FIG. 1 is a flow sheet for explaining a preferred embodiment of the method of the present invention. In the figure, 1... sieving, 2... roasting, 3... crushing, 4... leaching acid, 5... leaching, 6... solid-liquid separation, 7... insoluble matter, 8... solution, 9... Acid content removal, 10... Metastannic acid curing, 11... Oxidizing agent,
12...Inducing agent, 13...Solid-liquid separation, 14...
Metastannic acid, 15...roasted, 16...tin oxide,
17... Solution, 18... Neutralization, 19... Alkali neutralizing agent, 20... Solid-liquid separation, 21... Nickel hydroxide, 22... Nickel oxide, 23... Solution,
24...reduction, 25...metal tin, 26...metal nickel.

Claims (1)

【特蚱請求の範囲】  セラミツクス担䜓䞊にNiおよびSnを担持さ
せおなるNi−Sn系廃觊媒からNiおよびSnを分離
回収するにあたり、 (a) 前蚘廃觊媒を非酞化性の鉱酞で浞出するこず
により抜出されたNi分およびSn分を溶解含有
する酞液を埗、 (b) 工皋(a)の酞液から固圢分を陀去埌酞分を陀去
し、 (c) 工皋(b)の酞分を陀去した溶液をPHを1.0〜2.0
にするこずによりメタスズ酞を析出させ、 (d) 工皋(c)のメタスズ酞を懞濁含有する液を固−
液分離し、 (e) 工皋(d)で埗た固圢分を焙焌しお酞化スズを回
収し、 (f) 工皋(d)で埗た溶液をアルカリで䞭和するこず
により氎酞化ニツケルを析出させ、 (g) 工皋(f)の氎酞化ニツケルを懞濁含有する液を
固−液分離し、そしお (h) 工皋(g)で埗た固圢分を焙焌しお酞化ニツケル
を回収する こずを特城ずする方法。
[Claims] 1. In separating and recovering Ni and Sn from a Ni-Sn-based waste catalyst formed by supporting Ni and Sn on a ceramic carrier, (a) leaching the waste catalyst with a non-oxidizing mineral acid; (b) remove the solid content from the acid solution in step (a) and then remove the acid content; (c) remove the acid content from the acid solution in step (b). The pH of the solution from which acid has been removed is 1.0 to 2.0.
(d) The liquid containing metastannic acid suspended in step (c) is solidified.
(e) Roast the solid content obtained in step (d) to recover tin oxide; (f) Neutralize the solution obtained in step (d) with an alkali to recover nickel hydroxide. (g) solid-liquid separation of the liquid containing suspended nickel hydroxide in step (f), and (h) roasting the solid content obtained in step (g) to recover nickel oxide. A method characterized by:
JP57162645A 1982-09-18 1982-09-18 Method for separating and recovering nickel and tin from waste nickel-tin catalyst Granted JPS5953638A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57162645A JPS5953638A (en) 1982-09-18 1982-09-18 Method for separating and recovering nickel and tin from waste nickel-tin catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57162645A JPS5953638A (en) 1982-09-18 1982-09-18 Method for separating and recovering nickel and tin from waste nickel-tin catalyst

Publications (2)

Publication Number Publication Date
JPS5953638A JPS5953638A (en) 1984-03-28
JPS6366370B2 true JPS6366370B2 (en) 1988-12-20

Family

ID=15758553

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57162645A Granted JPS5953638A (en) 1982-09-18 1982-09-18 Method for separating and recovering nickel and tin from waste nickel-tin catalyst

Country Status (1)

Country Link
JP (1) JPS5953638A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0540072U (en) * 1991-11-06 1993-05-28 トキコ株匏䌚瀟 Brake fluid pressure control device

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
NL9301133A (en) * 1993-06-29 1995-01-16 Tno Process for recovering metals from AlêOë based catalysts.
KR100401995B1 (en) * 1998-12-23 2003-12-18 죌식회사 포슀윔 A METHOD FOR PRODUCING HIGH-PURITY NiO BY USING WASTE Ni ANODE
JP5511291B2 (en) * 2009-09-30 2014-06-04 ゚コシステム株匏䌚瀟 Method for purifying tin-containing waste and glass foam
CN120513310A (en) 2023-08-25 2025-08-19 高䞜亚铅株匏䌚瀟 Method for preparing nickel sulfate aqueous solution from nickel-containing raw material
CN120513308A (en) 2023-08-25 2025-08-19 高䞜亚铅株匏䌚瀟 Integrated nickel smelting method for recovering nickel oxide from nickel-containing raw material

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0540072U (en) * 1991-11-06 1993-05-28 トキコ株匏䌚瀟 Brake fluid pressure control device

Also Published As

Publication number Publication date
JPS5953638A (en) 1984-03-28

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