JPS60161339A - Recovering method of vanadium - Google Patents

Recovering method of vanadium

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Publication number
JPS60161339A
JPS60161339A JP1333284A JP1333284A JPS60161339A JP S60161339 A JPS60161339 A JP S60161339A JP 1333284 A JP1333284 A JP 1333284A JP 1333284 A JP1333284 A JP 1333284A JP S60161339 A JPS60161339 A JP S60161339A
Authority
JP
Japan
Prior art keywords
precipitate
ash
contg
ammonium salt
soln
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.)
Pending
Application number
JP1333284A
Other languages
Japanese (ja)
Inventor
Yatsuhiro Kawayoshi
川良 八紘
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 Corp
Original Assignee
Sumitomo Metal Industries 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 Sumitomo Metal Industries Ltd filed Critical Sumitomo Metal Industries Ltd
Priority to JP1333284A priority Critical patent/JPS60161339A/en
Publication of JPS60161339A publication Critical patent/JPS60161339A/en
Pending legal-status Critical Current

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  • Inorganic Compounds Of Heavy Metals (AREA)
  • Manufacture And Refinement Of Metals (AREA)

Abstract

PURPOSE:To recover Vanadium (expresses V hereunder) economically and efficiently by separating a V-contg. condensed precipitate from ash contg. V and blowing oxidizing gas therein and extracting the C-contents with an alkaline soln. and neutralizing it with CO2-contg. gas to remove the precipitate and thereafter adding ammonium salt. CONSTITUTION:V-contg. ash is separated by means of specific gravity to divide it into a suspended matter and precipitate in which the V-component is condensed and while blowing oxidizing gas (e.g. compressed air) in the precipitate, said V-component is extracted with an alkaline soln. Then, after condensing the V-enriched soln. with steam or the like, CO2-contg. gas is blown therein to neutralize it at about 8-9pH. After the precipitate is removed from the soln., ammonium salt (e.g. NH4Cl or the like) is added to recover the V-component as ammonium salt. By said method, V can be recovered almost completely at low cost.

Description

【発明の詳細な説明】 (発明の分野) 本発明は、■含有灰からのハづジウムの回収方法、特に
浮遊選鉱等による比重分離とアルカリ抽出とを組合−U
で構成した■含有灰からのバナジウムの回収方法に関す
る。
DETAILED DESCRIPTION OF THE INVENTION (Field of the Invention) The present invention is directed to (1) a method for recovering hadzium from containing ash, in particular a combination of specific gravity separation by flotation and alkali extraction;
1. Concerning a method for recovering vanadium from ash containing:

(従来技術) 重金属とし゛このバナジウムはその出尻な用途のため最
近多量に使用される領1iiJ (、こあり、新たな供
給源がめられている。しかし、資源としては限られた金
属であるため、従来のように石油原油に平均10〜10
0 ppm含有されているバナジウムを重油などの重質
残渣の燃焼灰から回収する方法におし」る改良が各種提
案されている。
(Prior art) Vanadium, a heavy metal, has recently been used in large quantities due to its basic uses. , an average of 10 to 10 to petroleum crude oil as in the past
Various improvements have been proposed to improve the method of recovering vanadium containing 0 ppm from the combustion ash of heavy residues such as heavy oil.

従来法としては、原理的には、(1)ソーダばい焼去、
(2)水酸化カリウム法、(3)a民法である酸抽出法
、(4)アルカリ抽出法、(5)酸アルカリ抽出法、(
61/8媒抽出法等がある。
In principle, the conventional method consists of (1) soda burning;
(2) Potassium hydroxide method, (3) A civil law acid extraction method, (4) Alkali extraction method, (5) Acid-alkali extraction method, (
There are methods such as 61/8 medium extraction method.

ここに、ソーダばい焼去は、■含有灰にソーダ塩を添加
してから700〜900 ’cて酸化ぽい焼した後、水
、酸あるいはアルカリでハーノジウムを抽出する方法で
ある。しかしながら、この方法にあっては、ばい焼温度
が高いため、■が溶融し、炉壁面等に融着する恐れがあ
り、それらを防止するために温度制御を厳密にする必要
がある。また、高温下でアルカリを使用しているためレ
ン力の浸食が大きい。その他、ソーダの一部が不純物と
反応するため有9JJ率が低くNa/Vの比を多くとる
必要があるばかりでなく、V205の飛散防止、SOX
、NOx等を111月yする必要からも、大型の集塵・
吸収機の設置が必要となる。
Here, soda burning is a method in which ① soda salt is added to the ash containing ash, oxidized burnt for 700 to 900 degrees Celsius, and then the harnodium is extracted with water, acid, or alkali. However, in this method, since the roasting temperature is high, there is a risk that (1) may melt and adhere to the furnace wall surface, etc., and it is necessary to strictly control the temperature to prevent this. In addition, since alkali is used at high temperatures, there is significant erosion due to oxidation. In addition, since some of the soda reacts with impurities, not only is the 9JJ ratio low and the Na/V ratio needs to be high, but also the prevention of V205 scattering and SOX
Large-scale dust collection and
It is necessary to install an absorber.

また、例えは、特開昭52−66812号に開示されて
いるよ・)に、水酸化カリウム法にあっても、ko+1
:仄−■・2というようにKOJ+が原料灰に対して多
量に必要となるばかりでなく、250〜400℃への昇
温6、二電気またはカス等のエネルギーも必要となる。
Also, for example, as disclosed in JP-A-52-66812), even in the potassium hydroxide method, ko+1
Not only is a large amount of KOJ+ required for the raw material ash, such as: 2 - 2, but also energy such as heating up to 250 to 400°C, 6, 2 electricity, or dregs is required.

さらに、混錬状態で加P()するので乾燥するに従って
乾燥粉か飛散するおそれがある。
Furthermore, since P() is added in a kneaded state, there is a risk that dry powder will scatter as it dries.

ところ−で、アルカリ抽出法はV含有灰を直接アルカリ
液に溶解してv分を抽出する方法であるか、抽出率が低
いため■が高濃度で含まれている使用ずめ1す4:媒に
ついてのみ適用か考えられているにすぎない。
By the way, the alkaline extraction method is a method in which the V-containing ash is directly dissolved in an alkaline solution to extract the V component, or because the extraction rate is low, it contains a high concentration of ■. It has only been considered that it applies only to mediums.

また酸抽出法は、p110〜0.3の範囲で原料灰中の
■、その他の有価金属を酸によって抽出する方法−ζあ
る。しかし、この方法乙こよれば大量の酸が必要となり
、また5i02等、不純物をも同時に多く抽出してしま
・うため後処理が複雑かつ面倒となる。
Further, there is an acid extraction method in which ① and other valuable metals in the raw material ash are extracted with acid in the range of p110 to 0.3. However, this method requires a large amount of acid and also extracts a large amount of impurities such as 5i02 at the same time, making the post-processing complicated and troublesome.

一方、酸アルカリ抽出法は、例えば特公昭45−228
06号に開示されているように、pHi、5〜4てHC
!、H3SO,等の酸に抽出後、60〜110℃に加熱
し、そのとき得られた沈殿物を次いてアルカリに熔かし
、そして再び酸を加えてpH1,5〜4.0としさらに
60〜110℃に加熱してV塩を析出・回収する方法で
ある。
On the other hand, the acid-alkali extraction method, for example,
As disclosed in No. 06, pHi, 5-4 and HC
! , H3SO, etc., heated to 60-110°C, the precipitate obtained at that time was then dissolved in alkali, and acid was added again to adjust the pH to 1.5-4.0. This is a method in which V salt is precipitated and recovered by heating to ~110°C.

しかしながら、この方法は、段階が複雑で、かつ薬品使
用量が多いため、実用的な方法とは云えない。
However, this method involves complicated steps and requires a large amount of chemicals, so it cannot be called a practical method.

(発明の目的) 本発明の目的とするところは、上述のような従来技術の
各欠点を解消したより経済的かつ効率的な■回収方法を
11供することである。
(Objective of the Invention) The object of the present invention is to provide a more economical and efficient recovery method that eliminates the drawbacks of the prior art as described above.

(発明の要約) ここに、本発明者らが」二連の目的を達成する方法につ
いて種々検討した結果、■含有灰ては例えば浮遊選鉱に
よって比重分離すると■のhツ縮率が著しく高くなるこ
とを見い出し、この点に着目してさらに研究開発を進め
たところ、以下の如く本発明で特定する各処理段階を組
合せて利用することにより従来よりはるかに高い回収率
で、しかもより安価に■が回収できることを見い出し本
発明を完成した。
(Summary of the Invention) As a result of various studies conducted by the present inventors on methods to achieve the two objectives, it was found that (1) When the ash containing ash is separated by specific gravity, for example, by flotation, the shrinkage ratio of (2) becomes significantly high. As a result of further research and development focusing on this point, we found that by combining the various processing steps specified in the present invention as described below, we can achieve a much higher recovery rate than before and at a lower cost. The present invention was completed based on the discovery that this can be recovered.

ずなわぢ、本発明ば: (al V含有灰を比重分離によって、浮遊物とV分が
濃縮された沈殿物とに分離回収する分離回収段階;(b
l l記(a1段階で分離回収された沈殿物を酸化性ガ
スを吹込みながらアルカリ液抽出するアルカリ抽出段階
; +Cj上記(h1段階−(得られた■含イ1tイν・\
co2含有ガスを吹き込め、中和する中和段階;および
(d)上記(C1段階で002吹込めにより中和された
V含イr lt炬Gご、沈殿物を除去してから、アンモ
ユウノ・塩を添加して■をアンモニウム塩として析出回
収する析出回収段階、 を包含する、■含有灰からのバナジウムの回収方法。
According to the present invention: (Separation and recovery step of separating and recovering al V-containing ash into floating matter and precipitate in which V content is concentrated by specific gravity separation; (b
l Note (alkaline extraction stage in which the precipitate separated and recovered in stage a1 is extracted with alkaline liquid while blowing oxidizing gas; +Cj above (h1 stage - (obtained
and (d) a neutralization stage in which CO2-containing gas is injected to neutralize it; A method for recovering vanadium from ash containing ■ a precipitation recovery step of adding and recovering ■ as an ammonium salt.

(発明の態様) 次に、添(;1図面の第1図は本発明に係る方法のフロ
ーソー1−を示すものである。以下、これに関連さ、1
て本発明をさらに具体的に説明する。
(Aspects of the Invention) Next, Figure 1 of the accompanying drawings shows a flow saw 1- of the method according to the present invention.
The present invention will now be described in more detail.

1iii記V含右灰は、例えはいわゆる重油燃焼灰(重
浦専焼灰、混焼法を含む)、アスファハ用−ピ、チ燃ハ
IL灰であるか、本発明にあっては必ずしもそれらにの
め制限されない。また、そのような燃焼灰にあっても、
炉内灰ばかりでなく、■含有率の著しく低い飛散灰をも
包含するものである。特に本発明によれは比重分離で■
濃縮率が非常に大きくとれるため、飛散灰などのような
低濃度のものに適用するとその実際上の効果が大きい。
Examples of the ash containing 1iii. There are no restrictions. Also, even in such combustion ash,
This includes not only in-furnace ash, but also fly ash, which has a significantly low content. In particular, according to the present invention,
Since the concentration ratio is very high, it has a great practical effect when applied to low concentration materials such as fly ash.

かかる■含有灰は重油燃焼炉内圧および1!i散灰とし
ては一般にそれぞれ第1表および第2表に示す組成を有
している。
Such ■Contained ash is the internal pressure of heavy oil combustion furnace and 1! The scattered ash generally has the composition shown in Tables 1 and 2, respectively.

40〜80 1〜71〜200〜33〜10cy−計 
ルー ul 九 10〜701〜50.5〜230〜603〜201〜8
まず本発明によれば■含有灰に刻し比重分離を行う。比
重分離には代表的には浮遊選鉱があるが、その他遠心分
離、凝集沈殿等によることもてきる。好ましくは浮遊選
鉱によって行う。以下本発明を灯油、パイン浦等の浮選
油を使って浮遊選鉱を行う場合を例にとって説明する。
40~80 1~71~200~33~10cy-total
Lou ul 910~701~50.5~230~603~201~8
First, according to the present invention, (1) the containing ash is chopped and subjected to specific gravity separation. Gravity separation typically involves flotation, but other methods such as centrifugation and coagulation and sedimentation can also be used. Preferably it is carried out by flotation. The present invention will be explained below by taking as an example the case where flotation is carried out using kerosene, Pineura or other flotation oil.

この浮遊選鉱によりC等を含む7F−遊物と、■、Ni
、 Fe等が濃縮された沈殿物とに分離される。なお、
好ましくは、このときの浮遊物にも■、Ni、 Fe等
が一部含有されているためアルカリ液で洗浄し、再回収
を図る。浮遊選鉱によるV分濃縮沈殿物を分QIJ、回
収する段階は、比重差によって■含有分を濃縮分離する
もの一ζあって、その限りにおいて、使用する厚選油、
温度、時間等の処理条件は特に制限されるものではない
Through this flotation, 7F-free substances containing C, etc., and ■, Ni
, and a precipitate in which Fe etc. are concentrated. In addition,
Preferably, since the suspended matter at this time also contains a portion of ■, Ni, Fe, etc., it is washed with an alkaline solution and recovered again. The step of recovering the V-concentrated precipitate from flotation involves concentrating and separating the content based on the difference in specific gravity.
Processing conditions such as temperature and time are not particularly limited.

このときの65選前の固形う〕および4選後の沈殿物中
の■含イj量の変化を第3表にまとめて示す。なお、表
出の例にあっては、出発原料としてv8〜10%を含む
V含有j火を使用した。
Table 3 summarizes the changes in the solid content before 65 selections and in the precipitate after 4 selections. In addition, in the example of expression, a V-containing fire containing V8 to 10% was used as a starting material.

第3表 (第3表、続き) (注)試験陽2.3は中和後浮選 浮遊選鉱により得られた■に冨む沈殿物は次いで、アル
カリ抽出段階において酸化性ガス、例えば圧縮空気を吹
き込みなからアルカリ液抽出するが、この抽出用アルカ
リ液としては、製鉄所での操業にあっては、その人手容
易性ということがら、好ましくは、溶銑のソーダ灰投入
による脱硫・脱リンスラグを水冷却して得たスラリーか
ら固形分を除去したものを有利に利用できる。なお、本
発明にあっては酸化性ガスを吹込みながらアルカリ抽出
を行うことがら、■溶出率は人中に向上する。
Table 3 (Table 3, continued) (Note) Test positive 2.3 is obtained by flotation after neutralization. The precipitate rich in The alkali solution is extracted by blowing the molten metal into the molten metal.As the alkali solution for extraction, desulfurization/dephosphorization slag by adding soda ash to the hot metal is preferably used for operation at a steelworks because of its ease of labor. A slurry obtained by cooling with water, from which the solid content has been removed, can be advantageously used. In addition, in the present invention, since alkaline extraction is performed while blowing in oxidizing gas, (1) the dissolution rate is improved.

ここに、第4表に示す組成のA、B二種の重油燃焼灰を
同しく第4表に示す組成を有1’/’)溶銑脱硫・脱リ
ン−1′ルカリ液を−I′ルカリ抽出液として使用し゛
ζアルカリ抽出した例を示す。このときのアルカリ液は
、ソーダ灰投入による脱硫・脱リンスラグを水冷却して
スラリー化したものから固形分を除去して得たアルカリ
液でpH9〜11、Na 2 、CO38= 10%を
含有するものであった。
Here, two types of heavy oil combustion ashes, A and B, having the compositions shown in Table 4 are used. An example of ζ-alkali extraction used as an extractant is shown below. The alkaline liquid at this time is an alkaline liquid obtained by removing the solid content from the desulfurization/dephosphorization slag made by adding soda ash and cooling it with water to form a slurry, and has a pH of 9 to 11 and contains Na 2 and CO38 = 10%. It was something.

第4表 (重量%) 旧訳アルカリ液1.5 II!当たり■含有灰1kgを
混合し、圧力5 = 7 kg/ cotの圧縮空気を
2e/m、il〕の割合で、6〜7時間アルカリ抽出浴
中るご投入した。浴/l!!t 度は60〜70゛〔シ
 こあっ)こ。
Table 4 (% by weight) Old translation alkaline solution 1.5 II! 1 kg of ash was mixed and compressed air at a pressure of 5 = 7 kg/cot was poured into an alkaline extraction bath at a rate of 2 e/m, il for 6 to 7 hours. Bath/l! ! The T degree is 60-70 ゛.

V含イ4灰−への場合について累積圧縮空気投入量とV
溶出率(%)との関係を第2図にグラフて示J−0V含
R灰−13の場合にも同様の仲間を示した。
Cumulative compressed air input and V for the case of V-containing 4 ash-
The relationship with elution rate (%) is shown graphically in FIG. 2, and a similar relationship was shown in the case of J-0V R-containing ash-13.

次に、補助酸化剤として過酸化水素を加え、圧縮空気と
の組合−已に、1つて■溶出率がとの程度改善される。
Next, hydrogen peroxide is added as an auxiliary oxidant, and in combination with compressed air, the elution rate is improved to the extent of (1).

かをめた。■含有灰−Aの場合について35%過酸化水
素の界不貞投入量(kg/V含有灰kg)に対し■溶出
率をプし!ノドして第3図に示す。第3図の場合、抽出
処理は60°Cで3時間行ったか、圧縮空気の吹き込め
は5時間行い、合a1て600a投入した。なお、■含
有灰−Bの場合にも同様の仰向を示した。
I bent down. ■For the case of ash-A, calculate the elution rate of 35% hydrogen peroxide (kg/kg of V-containing ash)! It is shown in Figure 3. In the case of Fig. 3, the extraction process was carried out at 60°C for 3 hours, or the blowing of compressed air was carried out for 5 hours, and a total of 600 a of air was used. Incidentally, in the case of ash-B containing ■, a similar upward orientation was also observed.

第3図に示′41−結果からも明らかなように、圧縮空
気が十分な量だυノ吹込まれれば、補助酸化剤は必すし
も必要とされない。
As is clear from the results shown in FIG. 3, if a sufficient amount of compressed air is blown, an auxiliary oxidizer is not necessarily required.

■分に冨む溶液は、次いで、必要により例えばスチーム
の投入によってV分が濃縮される。■分をほぼ3〜6%
としてから水添加の後にアルカリ性溶液として可溶化し
てから002含有カス、例えば燃焼廃カスを吹き込んで
例えばpHを8〜9とすることで中和する。
The solution enriched in (1) is then concentrated in (V) by, for example, introducing steam, if necessary. ■ Approximately 3-6% of the time
After adding water, the mixture is solubilized as an alkaline solution, and then neutralized by blowing in 002-containing residue, such as combustion waste residue, to adjust the pH to 8 to 9, for example.

CO2含有カス吹込みによる中和処理の結果を第5表に
まとめζ示ず。H2SO,tなどの薬剤を使用すること
なく、単に002含有ガスの吹込みだりでp)lを10
から8にまで低下させることができた。比較例として7
5%H2SO4を2.04kg/ Vkgおよび35%
H202を1.09kg/ V kg使用したときの■
収率も併せて示す。
The results of neutralization treatment by CO2-containing waste injection are summarized in Table 5 and are not shown. Without using chemicals such as H2SO, t, p)l can be reduced to 10 by simply blowing 002-containing gas.
We were able to reduce it from 8 to 8. 7 as a comparative example
5% H2SO4 2.04kg/Vkg and 35%
■ When using 1.09kg/V kg of H202
The yield is also shown.

またC02含有ガスの吹込み量とアルカリ液pl+の変
化との)ソ)連を第41ヌ1にグラフで不腐。この場合
にも、出発jぶjai’lとし゛(は■含イj仄(V−
5%)を使用し、こね」、す7分を30.61!/ Q
含イ+’する了ルカリン容、(kを41!i19し7−
(から、2I/minの11.り合−C1O%Cal、
含自ガスを吹込んだ。〆(シ?ll!t L;1.’ 
29〜35°(、ζあった。
In addition, the relationship between the amount of C02-containing gas blown and the change in alkaline solution PL+ is shown in a graph in No. 41 No. 1. In this case as well, the starting point is
5%) and knead for 7 minutes at 30.61! /Q
Contains i+' Ryo Karin Yong, (k is 41! i19 and 7-
(from 11.riai-C1O%Cal of 2I/min,
Injected with self-containing gas. 〆(shi?ll!t L;1.'
29-35° (,ζ was.

第5表 ざらに、上記脱水ケーキにはわずかにv分か随(1′さ
れているため、これを水洗することにより、あるいは必
要によりi;i述の゛rルカリ液抽出に使用したと同し
アルカリl&を使っC洗浄してもよい。
As shown in Table 5, since the dehydrated cake has a slight trace of v or 1', it can be washed with water, or if necessary, it can be washed with C cleaning may be performed using alkaline l&.

次@ニN1 、C7!等のアンモニウム塩を添加して■
う)をアンモニウム塩として回収する。この7分の析出
回収]1稈はすでに当業界においても良く知られている
ところであって、これ以」二の8及は不用であろう。
Next @ NiN1, C7! By adding ammonium salts such as ■
) is recovered as ammonium salt. This 7-minute precipitation recovery] 1 culm is already well known in the industry, and steps 2 and 8 will be unnecessary.

次に本発明を実施例によってさらに説明するが、これは
小に例示(あって、本発明を何ら制限するもの一ζない
ことは理iへvされるべき一ζある。
Next, the present invention will be further explained with reference to Examples, which are merely illustrative and should not be interpreted as limiting the present invention in any way.

)(屁ff1LI 第1図に示すフローチャー1に17怠って5%■の重油
燃焼か飛散灰1. OOk gを処理した。このときの
処理条イ11および7回収量(kg)は第6表にまとめ
C示ず。
) (Fartff1LI 1.OOkg of 5%■ heavy oil combustion or fly ash was treated by neglecting Flowchart 1 shown in Figure 1. At this time, the amount recovered (kg) in treatment rows 11 and 7 was Summary C not shown in table.

汰脆制) 本例では9%■の重油燃焼炉飛i1)灰100kgを実
施例1と同様にして処理した。このときの処理条件お、
Lひ7回収量(kg)は第7表にまとめて示す。
In this example, 100 kg of ash from a 9% heavy oil combustion furnace was treated in the same manner as in Example 1. Processing conditions at this time,
The amount of L-7 recovered (kg) is summarized in Table 7.

全回収率78% 全11.Ij収率80% このように、本発明に係る一連の工程により出発原料の
■含有灰からの■回収率は約80%である。
Total recovery rate 78% Total 11. Ij yield: 80% As described above, through the series of steps according to the present invention, the recovery rate (2) from the starting material (1)-containing ash is about 80%.

かくして、本発明に係る方法によれば、■はほは完全に
回収することができるばかりでなく、その回収費用も従
来のものと比較して、格別のエネルギーあるいは薬剤を
使用していないことからも容易に理解されるように、は
るかに少なくてすむ。また、湿式法のため、特別化合物
に指定されているv205の取扱が不用となるなど、本
発明は実用性の高い方法である
Thus, according to the method according to the present invention, not only can it be completely recovered, but the recovery cost is also lower than that of conventional methods because it does not use any special energy or chemicals. As is easily understood, much less is required. In addition, since it is a wet method, there is no need to handle v205, which is designated as a special compound, so the present invention is a highly practical method.

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

第1図は、本発明に係る方法のフローノート:第2図は
、アルカリ液抽出時の酸化性ガスの吹込量とV?8出率
との関係を示すグラフ;第3図は、同しく 8202投
入量と■溶出率との関係を示′Jグラフ;および 第4図は、CO。ガス投入量と/8液■)11との関係
を示すグラフである。 (al : if遊物と沈殿物との分離回収段階(b)
:アルカリ抽出段階 (C);中和段階 +d) : Vのアンモニウム塩の析出回収段階第1図 第2図 第3図 (ド)/Δヒず+リラ
Fig. 1 shows a flow note of the method according to the present invention; Fig. 2 shows the amount of oxidizing gas blown during alkaline liquid extraction and V? Figure 3 is a graph showing the relationship between the amount of 8202 input and the elution rate. It is a graph showing the relationship between the amount of gas input and /8 liquid (■)11. (al: if Separation and recovery stage (b) of free products and precipitates
: Alkaline extraction stage (C); Neutralization stage + d) : Precipitation and recovery stage of ammonium salt of V

Claims (1)

【特許請求の範囲】 (al V含有灰を比重分1ii11によって、/$遊
物とv分が/1% fiiiiされた沈殿物とに分離回
収j−る分冊を回収段階;tb+上記(a+段階て分離
回収された沈殿物を酸化性カスを吹込みながらアルカリ
液抽出するアルカリ抽出段階; (C)」1記(b1段階で得られた■含有液へ002含
有ガスを吹き込み、中和する中和段階;および(df 
l記(Cl段階でCO2吹込めにより中和された■含右
液に、沈殿物を除去してから、アンモこ−ラム塩を添加
してVをアンモニウム塩として析出回収する析出回収段
階、 を包含する、■含有灰からのハリシラJ、の回収方法。
[Scope of Claims] (Separation and collection of al V-containing ash into / $ free products and precipitate with v content of /1% fiii according to specific gravity 1ii11; tb + above (a + stage An alkaline extraction stage in which the precipitate separated and collected is extracted with an alkali solution while blowing in oxidizing residue; sum stage; and (df
(1) Precipitation recovery step in which precipitates are removed from the liquid containing liquid neutralized by CO2 injection in the Cl step, and ammonium salt is added to precipitate and recover V as an ammonium salt. ■ A method for recovering Harishira J from containing ash.
JP1333284A 1984-01-30 1984-01-30 Recovering method of vanadium Pending JPS60161339A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1333284A JPS60161339A (en) 1984-01-30 1984-01-30 Recovering method of vanadium

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1333284A JPS60161339A (en) 1984-01-30 1984-01-30 Recovering method of vanadium

Publications (1)

Publication Number Publication Date
JPS60161339A true JPS60161339A (en) 1985-08-23

Family

ID=11830179

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1333284A Pending JPS60161339A (en) 1984-01-30 1984-01-30 Recovering method of vanadium

Country Status (1)

Country Link
JP (1) JPS60161339A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103752419A (en) * 2014-01-26 2014-04-30 河南天罡实业有限公司 Method for flotation of vanadium pentoxide in fly ash
CN108636988A (en) * 2018-05-20 2018-10-12 英玖环境科技(成都)有限责任公司 The corundum slag solid waste comprehensive utilization of resources that vanadium iron production generates
US10648063B2 (en) 2016-09-06 2020-05-12 Iowa State University Research Foundation, Inc. Dissolution and separation of rare earth metals
CN111304466A (en) * 2020-03-11 2020-06-19 郑州大学 Method for selectively separating vanadium and chromium from vanadium and chromium-containing solution
WO2020218534A1 (en) * 2019-04-26 2020-10-29 川崎重工業株式会社 Method and system for processing combustion ash, and petroleum-based fuel combustion plant

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103752419A (en) * 2014-01-26 2014-04-30 河南天罡实业有限公司 Method for flotation of vanadium pentoxide in fly ash
US10648063B2 (en) 2016-09-06 2020-05-12 Iowa State University Research Foundation, Inc. Dissolution and separation of rare earth metals
CN108636988A (en) * 2018-05-20 2018-10-12 英玖环境科技(成都)有限责任公司 The corundum slag solid waste comprehensive utilization of resources that vanadium iron production generates
WO2020218534A1 (en) * 2019-04-26 2020-10-29 川崎重工業株式会社 Method and system for processing combustion ash, and petroleum-based fuel combustion plant
JP2020182890A (en) * 2019-04-26 2020-11-12 川崎重工業株式会社 Processing method and system for combustion ashes, and, petroleum-based fuel combustion plant
CN111304466A (en) * 2020-03-11 2020-06-19 郑州大学 Method for selectively separating vanadium and chromium from vanadium and chromium-containing solution

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