JPS636490B2 - - Google Patents
Info
- Publication number
- JPS636490B2 JPS636490B2 JP54153581A JP15358179A JPS636490B2 JP S636490 B2 JPS636490 B2 JP S636490B2 JP 54153581 A JP54153581 A JP 54153581A JP 15358179 A JP15358179 A JP 15358179A JP S636490 B2 JPS636490 B2 JP S636490B2
- Authority
- JP
- Japan
- Prior art keywords
- liquid
- sodium oxalate
- white mud
- mud slurry
- foam
- 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
Landscapes
- Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
Description
本発明は、バイヤー工程に於て、スラリー液よ
り蓚酸ナトリウムを除去するための蓚酸ナトリウ
ムの分離濃縮法に関する。
バイヤー法に於て、アルミナ含有鉱石から、ア
ルミナを製造する際、鉱石中に含まれる有機物、
ポリアクリル酸ソーダ等の沈降助剤、空気中の炭
酸ガス等が高温苛性アルミネート液中に溶解し、
Na、Ca、Al等と結合し有機酸塩となり、工程内
液中に蓄積していく。液中に有機物が蓄積してい
けば、アルミネート液中の平衡溶解度が高まり、
水酸化アルミニウムを析出させる際の析出率が悪
化し生産効率が低下し生産上重大な支障を生じ
る。
これを解決するには、液中の有機物濃度レベル
を低下させる為に、液中に有機物の最終形態であ
る炭酸ナトリウム、蓚酸ナトリウムの除去が通常
考えられている。
蓚酸ナトリウムは、過飽和アルミネート液より
水酸化アルミニウムを析出する際、析出初期に水
酸化アルミニウムと同時に微細結晶として晶出す
る。この固体蓚酸ナトリウムは固体水酸化アルミ
ニウムを含むアルミネート液(以降白泥スラリー
液と呼ぶ。)の水酸化アルミニウム粒子の沈降分
離性を悪化させる。その為にも蓚酸ナトリウムは
除去されねばならない。
白泥スラリー液中の固体蓚酸ナトリウムを除去
するためには、通常、白泥スラリー液を分級又は
清澄分離後、分級上液又は下液を濾過洗滌し、そ
の洗滌濾液を蓚酸除去工程に供給する。これは、
濾過ケーキ中に含まれる固体蓚酸ナトリウムを温
水で洗滌することにより、蓚酸ナトリウムが溶解
し、比較的多く蓚酸ナトリウムが含まれている洗
滌濾液が得られるので、この方法が蓚酸ナトリウ
ム除去の為に利用される。
この濾液の一部又は全量は、そのまま又は、濃
縮して直接消石灰と反応させたり、蓚酸ナトリウ
ム等の固体有機物を種子として、蓚酸ソーダ等の
有機物を析出させ、析出物を石灰と反応または焼
却して苛性ナトリウムの回収と有機物を除去する
ことが知られている。
上記蓚酸ナトリウムの除去に於て、洗滌濾液に
含まれている蓚酸ナトリウムの含有量が高けれ
ば、蓚酸ナトリウム除去効率又は、除去能率が向
上するのは明らかである。
その為には、白泥スラリー中の蓚酸ソーダ含有
量を高め、白泥スラリーの濾過洗滌液中に含まれ
る蓚酸ナトリウムの含有量を増大する必要があ
る。
固体蓚酸ナトリウムは、白泥スラリー中の細粒
水酸化アルミニウムに比較的多く付着することが
知られているので、分級等により比較的細粒を含
む白泥スラリー液を濾過洗滌することが考えられ
る。
本発明者等は、白泥スラリー液を分級する際、
白泥中に気泡を混入させ含泡沫白泥スラリー液を
分級装置に供給すれば浮上分離効果により通常の
分級に較べ2〜4倍蓚酸ナトリウムを濃縮できる
ことを発見した。
白泥スラリー液に空気等の気体を吹き込んで撹
拌し、かくして得られた含泡沫白泥スラリー液を
沈降管に入れ静置観察すれば、白泥スラリー液中
に無数の2mmφ以下の泡沫が存在している。その
まま放置しておけば、泡沫は、水酸化アルミニウ
ム粒子を包み込みながら浮上し、最終的に沈降管
上端より含泡沫粒子層、清澄アルミネート液層、
堆積粒子層に成相分離する。
この泡沫粒子部中の固体蓚酸ナトリウムは、原
液白泥スラリー液中の固体水酸化アルミニウムの
重量基準で2〜4倍濃縮される。
これは、気泡が白泥スラリー液に混入すること
により、固体蓚酸ナトリウム粒子が選択的に分離
濃縮されたものと考えられる。
泡沫を白泥スラリー液に混入させるには、浮遊
選鉱学の分野で知られている泡沫発生装置を利用
してもよく、また、白泥スラリー送液ポンプの吸
込側に空気等の気体を導入してもよい。更には、
白泥スラリー液貯槽に白泥スラリー液を投入する
際、空気等の気体を混入させる様な工夫を実施し
てもよい。いずれにしても2mmφ程度以下の微細
な泡沫を大量を混入させることが望ましいが、泡
沫の大きさ及び量は、白泥スラリーの状態(組成
濃度、固体の粒度等)に応じ、実験によつて定め
られる。
導入する気体としては好ましくは脱炭酸ガス処
理した空気、及び/又は窒素等苛性アルミネート
液に不活性の気体で、白泥スラリー液中の苛性ア
ルカリの炭酸化を起さない気体であることが必要
であるが、白泥スラリー液の発泡性が相当良いた
め、気体導入量も比較的少なく、事実上無処理大
気を用いて差し支えない。
以下に於て、本発明の実施例で更に詳細に説明
する。
実施例 1
固体濃度500g/、平均粒径45μの白泥スラ
リー液3を沈降管(15cmφ×40cm高さ)に入
れ、圧縮空気パイプの先端に接続したステンレス
粉末焼結体を沈降管底に沈め、該焼結体から発生
する微細な空気泡によつて白泥スラリーを撹拌し
た。空気送入量は0.1Nm3/分で10分間であつた。
空気送入を停止して10分間静置した後、沈降管内
には浮上分離した微細な泡沫を含む含泡沫粒子
層、その下方に清澄アルミネート液層、下方に沈
降堆積粒子層が画然と成相分離していた。上記含
泡沫粒子層を吸引採取して分析し、水酸化アルミ
ニウム固体濃度及び固体蓚酸ナトリウム含有率
(固体水酸化アルミニウム重量基準)を調べた
(A法)。
一方、比較のため、上記白泥スラリーに空気送
入を行はず、単に10分間静置した後、上記含泡沫
粒子層と同様の深さのスラリーを吸引採取して上
記同様の成分を分析した。(B法)その結果を第
1表に示す
The present invention relates to a method for separating and concentrating sodium oxalate for removing sodium oxalate from a slurry liquid in a Bayer process. In the Bayer method, when producing alumina from alumina-containing ore, organic matter contained in the ore,
Sedimentation aids such as sodium polyacrylate, carbon dioxide gas in the air, etc. dissolve in the high temperature caustic aluminate solution,
It combines with Na, Ca, Al, etc. to form organic acid salts and accumulates in the process liquid. As organic matter accumulates in the solution, the equilibrium solubility in the aluminate solution increases,
The precipitation rate when precipitating aluminum hydroxide deteriorates, production efficiency decreases, and serious problems occur in production. To solve this problem, it is usually considered to remove sodium carbonate and sodium oxalate, which are the final forms of organic matter in the liquid, in order to reduce the concentration level of organic matter in the liquid. When aluminum hydroxide is precipitated from a supersaturated aluminate solution, sodium oxalate crystallizes as fine crystals at the same time as aluminum hydroxide in the initial stage of precipitation. This solid sodium oxalate deteriorates the sedimentation and separation properties of aluminum hydroxide particles in an aluminate liquid containing solid aluminum hydroxide (hereinafter referred to as white mud slurry liquid). For this reason, sodium oxalate must be removed. In order to remove solid sodium oxalate from the white mud slurry, the white mud slurry is usually classified or clarified, the classified upper or lower liquid is filtered and washed, and the washed filtrate is supplied to the oxalic acid removal process. . this is,
By washing the solid sodium oxalate contained in the filter cake with warm water, the sodium oxalate is dissolved and a washed filtrate containing a relatively large amount of sodium oxalate can be obtained, so this method can be used to remove sodium oxalate. be done. A part or the entire amount of this filtrate may be used as it is, or after being concentrated and directly reacted with slaked lime, or by using solid organic matter such as sodium oxalate as a seed to precipitate organic matter such as sodium oxalate, and then reacting the precipitate with lime or incinerating it. It is known to recover caustic sodium and remove organic matter. In the above-mentioned removal of sodium oxalate, it is clear that if the content of sodium oxalate contained in the washing filtrate is high, the sodium oxalate removal efficiency or removal efficiency will be improved. For this purpose, it is necessary to increase the content of sodium oxalate in the white mud slurry and to increase the content of sodium oxalate contained in the filtered washing liquid of the white mud slurry. It is known that a relatively large amount of solid sodium oxalate adheres to the fine particles of aluminum hydroxide in the white mud slurry, so it is possible to filter and wash the white mud slurry liquid containing relatively fine grains by classification, etc. . The present inventors, when classifying white mud slurry liquid,
It has been discovered that by mixing air bubbles into white mud and supplying the foam-containing white mud slurry to a classifier, sodium oxalate can be concentrated by 2 to 4 times compared to conventional classification due to the flotation separation effect. If a gas such as air is blown into the white mud slurry liquid and stirred, and the thus obtained foam-containing white mud slurry liquid is placed in a sedimentation tube and observed, it is found that there are countless bubbles with diameters of 2 mm or less in the white mud slurry liquid. are doing. If left as it is, the foam will float to the surface while enveloping the aluminum hydroxide particles, and eventually a layer of foam-containing particles, a clear aluminate liquid layer,
Phase separation occurs into a layer of deposited particles. The solid sodium oxalate in the foam particle portion is concentrated 2 to 4 times based on the weight of solid aluminum hydroxide in the raw white mud slurry. This is considered to be because the solid sodium oxalate particles were selectively separated and concentrated due to the mixing of air bubbles into the white mud slurry liquid. To mix foam into the white mud slurry, a foam generator known in the field of flotation may be used, or a gas such as air may be introduced into the suction side of the white mud slurry pump. You may. Furthermore,
When the white mud slurry liquid is introduced into the white mud slurry liquid storage tank, a device such as mixing a gas such as air may be implemented. In any case, it is desirable to mix in a large amount of fine foam with a diameter of about 2 mm or less, but the size and amount of foam will depend on the condition of the white mud slurry (composition concentration, solid particle size, etc.) and will be determined through experiments. determined. The gas to be introduced is preferably decarbonized air and/or a gas that is inert to the caustic aluminate liquid, such as nitrogen, and is a gas that does not cause carbonation of the caustic alkali in the white mud slurry liquid. Although this is necessary, since the foamability of the white mud slurry liquid is quite good, the amount of gas introduced is relatively small, and in fact, untreated air can be used. In the following, the present invention will be explained in more detail using examples. Example 1 White mud slurry liquid 3 with a solid concentration of 500 g/m and an average particle size of 45 μm was put into a sedimentation tube (15 cmφ x 40 cm height), and the stainless steel powder sintered body connected to the tip of the compressed air pipe was sunk to the bottom of the sedimentation tube. The white mud slurry was stirred by fine air bubbles generated from the sintered body. The air feed rate was 0.1 Nm 3 /min for 10 minutes.
After stopping the air supply and allowing the tube to stand still for 10 minutes, a layer of foam-containing particles containing floated and separated fine bubbles was clearly visible in the sedimentation tube, a clear aluminate liquid layer below that, and a layer of sedimented particles below. There was phase separation. The foam-containing particle layer was collected by suction and analyzed to determine the aluminum hydroxide solid concentration and the solid sodium oxalate content (based on solid aluminum hydroxide weight) (Method A). On the other hand, for comparison, air was not introduced into the white mud slurry, but after it was simply allowed to stand for 10 minutes, the slurry at the same depth as the foam-containing particle layer was collected by suction and analyzed for the same components as above. . (Method B) The results are shown in Table 1.
【表】
従つて、泡沫を形成後静置させておけば3.2倍
固形蓚酸ナトリウムが濃縮したことが認められ
る。
実施例 2
白泥スラリー液(固体濃度400g/平均粒子
径40μ)は、第1図に示す導管6より導入されポ
ンプ3と導管7または8をへて貯槽1に供給され
る。そしてポンプ4より導管9をへて分級器2に
移され、ここで分級される。
導管7を経由すれば、貯槽1の液面上高所より
ラツパ状に白泥スラリー液が投入され空気を巻き
込んで貯槽1に落下する。(A法)または導管8
を経由すれば貯槽1の液面下に接続され、白泥ス
ラリー液に泡沫が混入しないようになつている。
(B法)A、B法とも実容積で200M3/Hの白泥
スラリー液を導管9より分級管2に導き、上昇速
度0.8M/Hとなるように分級管2の下抜き流量
を制御した。
この条件下において、A法の場合は、分級器2
内には、沈降粒子層の上部に清澄アルミネート液
層、その上部に浮上した含泡沫粒子層が形成され
ており、導管10から含泡沫粒子層が溢流分離さ
れた。一方B法の場合は、分級器2内には、上記
の含泡沫粒子層は形成されず、導管10から清澄
アルミネート液が溢流分離された。A法、B法に
おける導管10からの溢流を採取してその組成を
分析し、第2表の結果を得た。[Table] Therefore, it is recognized that solid sodium oxalate was concentrated by 3.2 times if the foam was allowed to stand after forming. Example 2 A white mud slurry liquid (solid concentration 400 g/average particle size 40 μm) is introduced from conduit 6 shown in FIG. 1 and supplied to storage tank 1 via pump 3 and conduit 7 or 8. Then, it is transferred from the pump 4 through the conduit 9 to the classifier 2, where it is classified. Through the conduit 7, the white mud slurry liquid is poured into the storage tank 1 from a high point above the liquid level and falls into the storage tank 1 while entraining air. (Method A) or conduit 8
It is connected below the liquid level of the storage tank 1 via the , to prevent foam from getting mixed into the white mud slurry liquid.
(Method B) For both methods A and B, white mud slurry liquid with an actual volume of 200 M 3 /H is introduced into the classification tube 2 through the conduit 9, and the underflow flow rate of the classification tube 2 is controlled so that the rising speed is 0.8 M/H. did. Under this condition, in the case of method A, the classifier 2
Inside, a clear aluminate liquid layer was formed above the settled particle layer, and a foam-containing particle layer floated above the liquid layer, and the foam-containing particle layer was overflowed and separated from the conduit 10. On the other hand, in the case of method B, the above foam-containing particle layer was not formed in the classifier 2, and the clarified aluminate liquid overflowed from the conduit 10 and was separated. The overflow from the conduit 10 in methods A and B was collected and analyzed for its composition, and the results shown in Table 2 were obtained.
【表】
第2表より、泡沫を混入した場合、固体水酸化
アルミニウム重量基準で2.55倍蓚酸ナトリウムが
濃縮したことになる。
以上の説明から明らかなように、本発明の方法
によれば前述の如き簡単な方法により、白泥スラ
リー液中の蓚酸ナトリウムの濃縮ができ、バイヤ
ー工程からの蓚酸ナトリウム除去の効率を飛躍的
に高めることが出来る。
本発明は、バイヤー工程液のもつ性質から、何
ら特殊な発泡剤を加えることなく、工業的に十分
な効果を奏しうるが、更に必要に応じて適宜発泡
剤を添加することにより一層大きな効果をあげう
ることはいうまでもない。[Table] From Table 2, when foam is mixed, sodium oxalate is concentrated by 2.55 times based on the weight of solid aluminum hydroxide. As is clear from the above explanation, according to the method of the present invention, sodium oxalate in the white mud slurry can be concentrated by the simple method described above, and the efficiency of sodium oxalate removal from the Bayer process can be dramatically improved. It can be increased. Due to the properties of the Bayer process liquid, the present invention can achieve sufficient industrial effects without adding any special blowing agent; however, even greater effects can be achieved by adding an appropriate blowing agent as necessary. Needless to say, I can give you a lot.
第1図は、この発明の実施例を説明する為の系
統図である。
1……スラリー貯槽、2……分級器、3,4,
5……ポンプ、6,7,8,9,10,11……
導管。
FIG. 1 is a system diagram for explaining an embodiment of the present invention. 1... Slurry storage tank, 2... Classifier, 3, 4,
5... pump, 6, 7, 8, 9, 10, 11...
conduit.
Claims (1)
水酸化アルミニウム粒子および蓚酸ナトリウム粒
子を含むスラリー液に空気、及び/又は不活性気
体を送入撹拌して、該スラリー液中に微細気泡を
混入し、ついで該微細気泡の浮上によつて液上層
に蓚酸ナトリウム粒子の富化した含泡沫粒子層を
形成せしめ、これを分離することを特微とするバ
イヤー工程スラリー液中の蓚酸ナトリウムの分離
濃縮法。1. In the Bayer process, air and/or inert gas is introduced and stirred into the slurry liquid containing the caustic aluminate liquid, aluminum hydroxide particles, and sodium oxalate particles to mix fine air bubbles into the slurry liquid. A method for separating and concentrating sodium oxalate in a Bayer process slurry liquid, which is characterized by forming a foam-containing particle layer enriched with sodium oxalate particles in the upper layer of the liquid by the floating of the microbubbles, and then separating this layer. .
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP15358179A JPS5678419A (en) | 1979-11-29 | 1979-11-29 | Separating and concentrating method of sodium oxalate in slurry liquor of bayer process |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP15358179A JPS5678419A (en) | 1979-11-29 | 1979-11-29 | Separating and concentrating method of sodium oxalate in slurry liquor of bayer process |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5678419A JPS5678419A (en) | 1981-06-27 |
| JPS636490B2 true JPS636490B2 (en) | 1988-02-10 |
Family
ID=15565610
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP15358179A Granted JPS5678419A (en) | 1979-11-29 | 1979-11-29 | Separating and concentrating method of sodium oxalate in slurry liquor of bayer process |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5678419A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2002094715A1 (en) * | 2001-05-18 | 2002-11-28 | Beijing University Of Chemical Technology | Ultrafine modified aluminium hydroxide and its preparation |
| CN103030160B (en) * | 2012-12-11 | 2014-11-05 | 中国科学院过程工程研究所 | Method for recycling alumina and sodium oxide from bayer process red mud |
-
1979
- 1979-11-29 JP JP15358179A patent/JPS5678419A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5678419A (en) | 1981-06-27 |
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