JPH06507206A - Desiliconization method for inorganic aqueous solution - Google Patents
Desiliconization method for inorganic aqueous solutionInfo
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- JPH06507206A JPH06507206A JP4509113A JP50911392A JPH06507206A JP H06507206 A JPH06507206 A JP H06507206A JP 4509113 A JP4509113 A JP 4509113A JP 50911392 A JP50911392 A JP 50911392A JP H06507206 A JPH06507206 A JP H06507206A
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- C—CHEMISTRY; METALLURGY
- C23—COATING METALLIC MATERIAL; COATING MATERIAL WITH METALLIC MATERIAL; CHEMICAL SURFACE TREATMENT; DIFFUSION TREATMENT OF METALLIC MATERIAL; COATING BY VACUUM EVAPORATION, BY SPUTTERING, BY ION IMPLANTATION OR BY CHEMICAL VAPOUR DEPOSITION, IN GENERAL; INHIBITING CORROSION OF METALLIC MATERIAL OR INCRUSTATION IN GENERAL
- C23G—CLEANING OR DE-GREASING OF METALLIC MATERIAL BY CHEMICAL METHODS OTHER THAN ELECTROLYSIS
- C23G1/00—Cleaning or pickling metallic material with solutions or molten salts
- C23G1/36—Regeneration of waste pickling liquors
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01G—COMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
- C01G49/00—Compounds of iron
- C01G49/02—Oxides; Hydroxides
- C01G49/06—Ferric oxide [Fe2O3]
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2004/00—Particle morphology
- C01P2004/60—Particles characterised by their size
- C01P2004/62—Submicrometer sized, i.e. from 0.1-1 micrometer
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- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2006/00—Physical properties of inorganic compounds
- C01P2006/80—Compositional purity
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Abstract
(57)【要約】本公報は電子出願前の出願データであるため要約のデータは記録されません。 (57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.
Description
【発明の詳細な説明】 無機質水溶液の脱珪方法 本発明は、無機質水溶液、特に酸洗い用水溶液の脱珪方法、シリカ含有量を減少 させた酸化鉄の製造方法、特にフェライトの製造方法に関する。[Detailed description of the invention] Desiliconization method for inorganic aqueous solution The present invention provides a method for desiliconizing inorganic aqueous solutions, especially aqueous solutions for pickling, and reducing the silica content. The present invention relates to a method for producing iron oxide, in particular a method for producing ferrite.
消費された酸洗い用水溶液を再生させる技術分野において、スプレィ焙焼技術を 用いることが知られている。この方法において、特に電子工業のだめの先駆物質 (フェライト組織)として役立つ酸化鉄I[1(Fe20s)を回収することが 可能である。これらの鉄酸化物セラミックスの電子的(電磁気的)性質は、主と して材料のシリカ含有量に左右される。従って、現在では、軟質のフェライトの 適用のため、鉄酸化物中のシリカ含有量(Sin2)か0.01%を越えないこ とか電子工業により要求されるが、他方はんの数年前にはこの限界は0.02% の範囲内にあった。鉄酸化物の分野における開発は、この限界を更に低下させる ことを可能にする。従って、非常に純粋な鉄酸化物の粉末(最大0.01%のS iO□)の価格は、1トン当たり約4900オーストリア シンクと考えられる が、従来のプラントにて製造されたような、約0.05%SiO□含有量を有す る鉄酸化物は、1トン当たり約700オーストリア シンク乃至約950オース トリア シンクの価格になる。In the technical field of regenerating the consumed pickling solution, we are developing spray roasting technology. known to be used. In this method, especially the precursors of the electronic industry It is possible to recover iron oxide I[1 (Fe20s), which serves as a ferrite structure. It is possible. The electronic (electromagnetic) properties of these iron oxide ceramics are mainly depends on the silica content of the material. Therefore, at present, soft ferrite For application, the silica content (Sin2) in iron oxide must not exceed 0.01%. is required by the electronics industry, but on the other hand, a few years ago this limit was 0.02%. was within the range. Developments in the field of iron oxides will further reduce this limit. make it possible. Therefore, very pure iron oxide powder (up to 0.01% S The price of iO□) is thought to be approximately 4,900 Austrian sinks per ton. has a content of approximately 0.05% SiO□, as produced in a conventional plant. Iron oxides range from about 700 Au sinks to about 950 Au sinks per ton. This is the price of the Tria sink.
シリカを含む水の処理のための装置及び方法は、特公昭59−90688号から 知られており、それによればシリカを含む原水が2つの濾過段階を通され、その 第1濾過段階は微細孔膜又はウルトラ フィルタ膜を備え、第2濾過段階は逆浸 透膜を備えている。この方法は、水中にある最大粒度1ミクロン以上の微細子を 捕捉しうるか、通常の形の珪酸は、その粒度が0.02 ミクロン以下であるの て分離することができない。更に、高い含有量の付加的成分を存する酸洗い用水 溶液の脱珪にこの方法を適用しつるという暗示も与えられていない。Apparatus and method for treating water containing silica are disclosed in Japanese Patent Publication No. 59-90688. is known, according to which raw water containing silica is passed through two filtration stages; The first filtration stage is equipped with a microporous membrane or ultrafiltration membrane, and the second filtration stage is a reverse filtration stage. Equipped with a permeable membrane. This method removes microscopic particles with a maximum particle size of 1 micron or more in water. Silicic acid in its normal form, which can be trapped, has a particle size of less than 0.02 microns. cannot be separated. In addition, pickling water with a high content of additional components Nor is there any suggestion that this method be applied to solution desiliconization.
従って、少し前にも、酸洗い溶液の脱珪方法か提案され、工業的ブランl−にお いて採用さ第1、夫々テストされた。これらの方法は例えばオーストリ特許第3 80675号に記載されているが、この方法は、ビックリング酸(pickl− ing acid)に3まれでいる塩化鉄の一部(約1〜2%)を水酸化鉄の形 で析出(沈殿)させ、同時にコロイド状珪酸の吸収的共沈を行わせることに基つ いている。然しなから、この方法は、高価な装置と技術的費用を必要とすると共 に、大量のスラッジを回収してこれを処分しなけれはならない、という欠点かあ る。更に化学製品(例えばアンモニア凝集剤)の消費か比較的に多く、そのため 、この方法を実施するためのプラントは、比較的に高価であり、特に経済的では ない。従って、全ブラントコス)・に対するスプレィ焙焼設備の出資割合は約2 0〜30%に達する。Therefore, some time ago, a method for desiliconization of pickling solutions was proposed and used in industrial bran l-. They were first adopted and tested respectively. These methods are described, for example, in Austria Patent No. No. 80675, this method uses Bickling acid (pickl- A part of the iron chloride (approximately 1 to 2%), which is rare in ing acid), is converted into iron hydroxide form. It is based on the fact that colloidal silicic acid is precipitated (precipitated) at the same time as colloidal silicic acid is co-precipitated by absorptive co-precipitation. I'm there. However, this method requires expensive equipment and technical costs, and However, the disadvantage is that a large amount of sludge must be collected and disposed of. Ru. Furthermore, the consumption of chemical products (e.g. ammonia flocculants) is relatively high, so , the plant for implementing this method is relatively expensive and not particularly economical. do not have. Therefore, the investment ratio of spray roasting equipment to the total brand cost is approximately 2 It reaches 0-30%.
本発明の目的は、それ故、任意の無機質水溶液からその中に含まれている珪酸の 分離を、化学製品や労働コストを避けながら比較的安価に行うことを可能にする 方法を提供することである。更にもう1つの目的は、鉄酸化物の製造のための簡 単な方法において、この鉄酸化物が電子工業により要求されるソリ力の限界値を 越えないことを特徴とする簡単な鉄酸化物の製造方法を提供することである。こ の方法は、消費されたピックリング(酸洗い用)溶液の再生(好ましくは鉄酸化 物の回収)のための現存する方法に組み込むのに適当であるように意図された。The object of the present invention is therefore to extract from any inorganic aqueous solution the silicic acid contained therein. Allows separation to be performed relatively cheaply while avoiding chemicals and labor costs The purpose is to provide a method. Yet another objective is to provide a simple method for producing iron oxides. In a simple way, this iron oxide can meet the warping force limits required by the electronics industry. It is an object of the present invention to provide a simple method for producing iron oxide, which is characterized by not exceeding the above. child The method involves regenerating the spent pickling solution (preferably iron oxidation It is intended to be suitable for integration into existing methods for the recovery of materials.
第1の目的を達成するために、本発明は、処理されるき溶液を直交流(cros s−f low)フィルタに遠し、60〜90℃の温度好ましくは70〜80° Cの温度で該フィルタを通過させる。In order to achieve the first objective, the present invention provides a cross flow (cross flow) solution to be treated. s-f low) far from the filter, temperature of 60-90°C, preferably 70-80° Pass through the filter at a temperature of C.
水溶液中に存在する珪酸は、直交流フィルタ内で支配的な条件下で、主として支 配的な温度下てミセル(micelular)構造に変換される。これらのポリ マーの組織は、水化形態て存在し、静電荷より懸濁状部に維持される。これらの 直径は、数十ミクロンないし数百ミクロンに達する。Silicic acid present in aqueous solutions is mainly supported under the conditions prevailing in cross-flow filters. It is converted into a micellar structure under moderate temperature. These poly The mer tissue exists in a hydrated form and is kept in suspension by electrostatic charges. these The diameter reaches tens to hundreds of microns.
珪酸のミセル構造の大きさのおかげで、微細瀘過即ぢマイクロ フィルトーンヨ ンのためにも利用できる微細濾過のための範囲は、0.02 ミクロンと10ミ クロンとの間の分離可能な粒度を含んでいる。このようなフィルタの膜は現在種 々の材料から製造されており、生化学的用途に対してはセルローズ誘導体か用い られるが、本発明に従って採用さるような直交流濾過の技術のためには、主とし て、ポリプロピレン、ポリエチレン又はポリスルフォンからなる合成樹脂膜が採 用される。中空のファイバ、発泡ガラス又は多孔質セラミック材料もまた用いる ことができる。Thanks to the size of the micellar structure of silicic acid, micro filtration can be easily achieved. The range for fine filtration, which is also available for microfiltration, is 0.02 micron and 10 micron. Contains separable particle sizes between chlorine and chlorine. The membranes of such filters are currently For biochemical applications, cellulose derivatives or cellulose derivatives are used. However, for cross-flow filtration techniques such as those employed in accordance with the present invention, the main Therefore, a synthetic resin membrane made of polypropylene, polyethylene or polysulfone is adopted. used. Hollow fibers, foam glass or porous ceramic materials are also used. be able to.
直交流濾過の原理は、懸濁又は乳化させた成分を含有する液体の処理のためにも それ自体知られている。フィルタ要素のフィルタケーキ上の被覆は、静的濾過条 件下では濾過液の流量を絶えず増減させるが、直交流濾過においては、平衡条件 を越えて濾過方向に対し横断的に電圧勾配により及はされる力によりこの被覆は 妨げられる。これにより、長期間にわたり高い濾過液流量で濾過を行うことが可 能となる。更に、定期的な逆流即ち濾過工程の短期間の逆転により、この被覆を フィルタ要素の表面から実質的に解放し除去することができ、それによってもと の濾過能力を回復させることができる。然しなから、水溶液中に含まれる珪酸を 、直交流フィルタによる分離を可能とするような構造に変換することは、最初は 予想もてきなかった。然しなから、上述の条件下で、直径が数百オングストロー ムを越えるミセル構造の形成か起こり、従って、従来の0.2ミクロンのポリプ ロピレン膜のホースを用いて、珪酸の事実上完全な分離が可能である。The principle of cross-flow filtration is also applicable for the treatment of liquids containing suspended or emulsified components. itself known. The coating on the filter cake of the filter element is Under conditions, the flow rate of the filtrate is constantly increased or decreased, but in cross-flow filtration, the equilibrium condition is The force exerted by the voltage gradient transverse to the filtration direction beyond be hindered. This allows filtration to be performed at high filtrate flow rates for long periods of time. Becomes Noh. Additionally, periodic backflow or short-term reversal of the filtration process can remove this coating. can be substantially released and removed from the surface of the filter element, thereby filtration ability can be restored. However, the silicic acid contained in the aqueous solution , converting it into a structure that allows separation by a cross-flow filter is initially I couldn't have predicted it. However, under the conditions described above, the diameter of the straw The formation of a micellar structure that exceeds that of the conventional 0.2 micron polyplast occurs. Virtually complete separation of the silicic acid is possible using a lopyrene membrane hose.
本発明による方法は、消費された酸洗い溶液の再生工程に特に有利に組入れるこ とができ、その際、酸洗い溶液から回収された酸化鉄はほとんどシリカを含まず それ放電子工業の目的のために極めて適しているという利点がある。その目的の ために、本発明は、無機質水溶液特に、溶解した鉄並びに珪酸を著しく含有する 使用済みの酸洗い溶液を、60〜90°C好ましくは70〜80°Cて直交流フ ィルタを通過させ、その後スプレィ焙焼法により、0.01%以下の珪酸を含有 する対応する酸化物に変換される。The method according to the invention can be particularly advantageously incorporated into the regeneration process of the spent pickling solution. The iron oxide recovered from the pickling solution contains almost no silica. It has the advantage of being extremely suitable for purposes in the electronics industry. of that purpose Therefore, the present invention is suitable for aqueous inorganic solutions, in particular those containing significantly dissolved iron and silicic acid. The used pickling solution is heated to 60-90°C, preferably 70-80°C, through a cross-flow filter. Contains 0.01% or less of silicic acid by passing through a filter and then using a spray roasting method. is converted into the corresponding oxide.
両方の工程において、濃縮液を直交流フィルタの中へ再循環させるのが好ましい 。これにより、フィルタの分離効果を更に高めて濾過液の純度を改善することが できる。In both steps, it is preferred to recirculate the concentrate into the cross-flow filter. . This further enhances the separation effect of the filter and improves the purity of the filtrate. can.
次の説明において、使用済みの酸洗い酸から酸化鉄を製造するための方法の好ま しい実施例を、添付図面を参照して更に説明する。In the following description, a preferred method for producing iron oxide from used pickling acid will be presented. New embodiments will be further described with reference to the accompanying drawings.
第1図は、脱珪をまとめてピンクリング酸を再生するためのプラントの概略線図 である。Figure 1 is a schematic diagram of a plant for regenerating pink phosphoric acid by combining desiliconization. It is.
第2図は、直列に接続した2つのフィルタユニットをもっ脱珪用プラントの詳細 線図である。Figure 2 shows details of a desiliconization plant with two filter units connected in series. It is a line diagram.
処理されるへき溶液は、手製縮機2と、手製縮機の槽を構成する予収集容器3と を通過させた後、スプレィロース1−リアクタl内でスプレィ焙焼される。それ により形成された固体反応生成物即ち金属酸化物は、引出し装置!■によって取 り出されるが、他方、気体反応生成物は、好ましくは静電フィルタ12を経て手 製縮機2へ戻される。手製縮機(これはルアシイ(Lurji)型又はヘンチュ リ(Venturi)型でよい)から、導管は、2つの液滴分離機4・\通し、 そこから吸収塔5.6へ導かれ、該吸収塔の中でビックリング酸が回収される。The filtration solution to be processed is collected in a hand-made shrinking machine 2 and a pre-collection container 3 that constitutes a tank of the hand-made shrinking machine. After passing through, it is spray roasted in the spray roast 1-reactor 1. that The solid reaction product, i.e. metal oxide, formed by the extraction device! ■ taken by On the other hand, the gaseous reaction products are preferably passed through an electrostatic filter 12 and then manually removed. It is returned to the shrinking machine 2. Hand-made shrinking machine (this is a Lurji type or Hentsch type) The conduit passes through two droplet separators 4. From there it is led to an absorption column 5.6 in which the bicking acid is recovered.
これらの吸収塔5.6からの廃ガスは結局は、2つの液滴分離機7を経て外部環 境へ排出される。The waste gas from these absorption towers 5.6 eventually passes through two droplet separators 7 to the outer ring. discharged to the border.
然しなから、予収集容器3からの手製縮溶液は、二者択一的に、ポンプ31によ って直交流フィルタ(cross−flow filter) 8へ通してもよ い。However, the homemade condensation solution from the pre-collection container 3 can alternatively be pumped by the pump 31. You can also pass it through cross-flow filter 8. stomach.
この場合、ポンプ81は、直交流フィルタ8を経て濃縮液を繰り返し循環させる のに役立つ。In this case, the pump 81 repeatedly circulates the concentrate through the cross-flow filter 8. useful for.
第2図に線図て示すように、2つ(又はそれ以上)のフィルタユニット(8a及 び8b)を直列に取付けてもよい。As shown diagrammatically in Figure 2, two (or more) filter units (8a and and 8b) may be installed in series.
実 施 例 第1図の線図に従って構成されたビックリング酸再生プラントにおいて、組成( 及びスプレィ焙焼工程の後に得られる理論的酸化物の組成)の消費されたビック リング酸が処理を受けた。Example In a Bickling acid regeneration plant configured according to the diagram in Figure 1, the composition ( and the theoretical oxide composition obtained after the spray torrefaction process). The phosphoric acid was treated.
1、ICP分析: 結果として生ずる理論的酸化物の組成 Fe : 87 g/l Fears 99.16%Cr : 0.03 Cr 2(is 352 ppmNi : 0.02 Ni0 204 Al: 0.05 AI。01 760S+Ot 0.036 5102 28 9Mn : 0.27 Mn0 2800Ca : 0.08 Ca0 900 Zn : 0.06 Zn0 598 Mg : 0.16 Mg0 2315pb・ o、 oo pbo o。1. ICP analysis: The resulting theoretical oxide composition Fe: 87 g/l Fears 99.16% Cr: 0.03 Cr 2 (is 352 ppm Ni: 0.02 Ni0 204 Al: 0.05 AI. 01 760S+Ot 0.036 5102 28 9Mn: 0.27 Mn0 2800Ca: 0.08 Ca0 900 Zn: 0.06 Zn0 598 Mg: 0.16 Mg0 2315 pb・o, oo pbo o.
Cu : 0.025 Cu0 221全HCI: 197g/I (約20% )理論的最大CF 値:0.15%バウンド直交流フィルタ(cross−fi lter)は濃縮液回路に直接に組み込まれた。Cu: 0.025 Cu0 221 Total HCI: 197 g/I (approx. 20% ) Theoretical maximum CF value: 0.15% bound cross-fi filter (cross-fi lter) was integrated directly into the concentrate circuit.
濃縮液回路における処理量の能力は28001V/hに達し、フィルタの処理量 能力は20001 / hに達した。13時間と17時間の夫々の運転時間の後 、鉄の濃度及びシリカの濃度の夫々について下記の値が得られた。The throughput capacity of the concentrate circuit reaches 28001V/h, and the throughput of the filter The ability reached 20001/h. After 13 and 17 hours of driving time respectively. , the following values were obtained for each of the iron concentration and silica concentration.
a)=Fe(2+)in g/1. b =Fe(3+)in g/1. c) =SiOz in mg/l濃縮液 透過液 a) b) c) a) b) c) −−−−110,217,542 13h 108.2 22.3 25 106.6 20.8 22.5(+2 24−148pp/酸化物)17h 111.3 23.3 27.6 117 .3 23.9 22.9(114−137ppm/酸化物)次の実験において 、ビックリング酸か処理されたが、その濃度の値は次の通りであった Fe(2 +)79.9 g/1. Fe(3+) 5.6 g/1. Si0□38 m g/I (これは、酸化物中の337ppmの理論的最大値に相当する)。直交 流濾過を用いて1時間以内に及び4時間の経過後の夫々において次の値が得られ た:濃縮液 透過液 a) b) c’) a) b)c) Ih 113.0 24.6 27.0 1!7.5 25.8 15.5(7 6−92ppm/酸化物)4h 117.5 27.2 37.5 +18.3 27.6 22.8(109−135ppm/酸化物)その後、直交流フィル タをスイッチ・オフし、更に4時間後次の値が得られた。a)=Fe(2+)in g/1. b=Fe(3+)in g/1. c) =SiOz in mg/l concentrate permeate a) b) c) a) b) c) -----110,217,542 13h 108.2 22.3 25 106.6 20.8 22.5 (+2 24-148pp/oxide) 17h 111.3 23.3 27.6 117 .. 3 23.9 22.9 (114-137 ppm/oxide) in the following experiment , Bickling acid was treated, and the concentration values were as follows: Fe(2 +)79.9 g/1. Fe(3+) 5.6 g/1. Si0□38m g/I (which corresponds to the theoretical maximum of 337 ppm in the oxide). orthogonal Using flow filtration, the following values were obtained within 1 hour and after 4 hours, respectively. : Concentrate, permeate a) b) c’) a) b) c) Ih 113.0 24.6 27.0 1!7.5 25.8 15.5 (7 6-92ppm/oxide) 4h 117.5 27.2 37.5 +18.3 27.6 22.8 (109-135 ppm/oxide) Then cross-flow filter The meter was switched off and after a further 4 hours the following values were obtained.
濃縮液 透過液 a)b)c)a)b)c) 4h 113.8 32.4 56.2(1) 39(350ppm/酸化物) 上記の表において、引き出された全酸化物中のシリカについてのデータにおいて 、酸化物は溶液からの外挿により珪酸された。従って、スプレィ焙焼酸化物につ いての分析結果を以下に示す。Concentrated liquid Permeated liquid a) b) c) a) b) c) 4h 113.8 32.4 56.2 (1) 39 (350ppm/oxide) In the table above, in the data for silica in the total oxide drawn , the oxide was silicified by extrapolation from solution. Therefore, regarding spray roasted oxide The analysis results are shown below.
Fe : Fe*O* : 99.2%Mn : 3093 ppm MnO: 0.399%SiOx : 100 5i02: 0.010%(最大値)V : 141 V2O5: 0.025Ti : 95 Ti0z: 0.0+ 6Cr : 338 Crz02: 0.050Cu : +74 Cub: 0.021Ni、 166 Nip+ 0.021Co : 23 Cod: 0.029Pb : 26 PbO: o、 003Zn : 246 ZnO : 0.031Al : 749 Al2O2: 0.139Ca : 766 Cao: 0.108Mg : 692 Mg0 0.128P : 30 PzOs O,007 l□□−’PCT/^T 92100069フロントページの続き (72)発明者 ガムスリーグラ、マンフレッドオーストリー国、ウィーン エ イ−1220゜ルギールシュトラーセ 28/ 3 /12(72)発明者 ク ラドニッヒ、ヴオルガングオーストリー国、セント ゲオルゲン エイ−422 2,ルフテンベルグ 65Fe: Fe*O*: 99.2% Mn: 3093 ppm MnO: 0.399% SiOx: 100 5i02: 0.010% (maximum value) V : 141 V2O5: 0.025Ti: 95 Ti0z: 0.0+ 6Cr: 338 Crz02: 0.050Cu: +74 Cub: 0.021Ni, 166 Nip+ 0.021Co: 23 Cod: 0.029Pb: 26PbO: o, 003Zn: 246ZnO : 0.031Al: 749 Al2O2: 0.139Ca: 766 Cao: 0.108Mg: 692 Mg0 0.128P: 30 PzOs O,007 l□□-’PCT/^T 92100069Continuation of front page (72) Inventor: Gumsligra, Manfred Austria, Vienna et al. E-1220゜Lugierstrasse 28/3/12 (72) Inventor Ku Radnig, Austria, St. Georgen A-422 2, Luftenberg 65
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AT0098191A AT395408B (en) | 1991-05-13 | 1991-05-13 | MICROFILTRATION |
AT981/91 | 1991-05-13 | ||
PCT/AT1992/000069 WO1992020834A1 (en) | 1991-05-13 | 1992-05-13 | Method for the desilification of aqueous inorganic solutions |
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JPH06507206A true JPH06507206A (en) | 1994-08-11 |
JP2810234B2 JP2810234B2 (en) | 1998-10-15 |
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JP4509113A Expired - Fee Related JP2810234B2 (en) | 1991-05-13 | 1992-05-13 | Desiliconization method of inorganic aqueous solution |
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EP (1) | EP0584146A1 (en) |
JP (1) | JP2810234B2 (en) |
KR (1) | KR0138070B1 (en) |
CN (1) | CN1037705C (en) |
AT (1) | AT395408B (en) |
TW (1) | TW222610B (en) |
WO (1) | WO1992020834A1 (en) |
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DE19829592C1 (en) * | 1998-07-02 | 1999-12-09 | Umweltanalytisches Zentrum Gro | Mineral acids containing metals from pickling plants are processed and recovered |
AT411575B (en) * | 2002-07-25 | 2004-03-25 | Kcs Austria Engineering Gmbh | Regeneration of steelworks spray-roasting pickling solutions, comprises filtering settled solution using transverse-flow microfilter |
FR2916205A1 (en) * | 2007-05-16 | 2008-11-21 | Siemens Vai Metals Tech Sas | INSTALLATION AND PROCESS FOR TREATING SILICON STEEL BAND REMOVAL SOLUTIONS |
AT13601U1 (en) * | 2012-09-06 | 2014-04-15 | Astec Engineering Gmbh | Purification and desiccation of spent acid baths using combined microfiltration techniques |
CN110272159A (en) * | 2019-06-17 | 2019-09-24 | 苏州乔发环保科技股份有限公司 | The recycling processing method and device of inorganic salts in a kind of industrial wastewater |
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JPS5990688A (en) * | 1982-11-15 | 1984-05-25 | Arubatsuku Service Kk | Device and method for treating silica-containing water |
FR2670508B1 (en) * | 1990-12-13 | 1994-08-12 | Siderurgie Fse Inst Rech | PROCESS FOR SEPARATING THE SILICON COMPOUNDS CONTAINED IN A HYDROCHLORIC STRIPPING BATH OF PARTS, PARTICULARLY STEEL SHEETS. |
-
1991
- 1991-05-13 AT AT0098191A patent/AT395408B/en not_active IP Right Cessation
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1992
- 1992-05-13 CN CN 92104547 patent/CN1037705C/en not_active Expired - Fee Related
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- 1992-05-13 EP EP19920909956 patent/EP0584146A1/en not_active Withdrawn
- 1992-05-13 WO PCT/AT1992/000069 patent/WO1992020834A1/en not_active Application Discontinuation
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WO1992020834A1 (en) | 1992-11-26 |
CN1068602A (en) | 1993-02-03 |
ATA98191A (en) | 1992-05-15 |
CN1037705C (en) | 1998-03-11 |
TW222610B (en) | 1994-04-21 |
AT395408B (en) | 1992-12-28 |
EP0584146A1 (en) | 1994-03-02 |
KR0138070B1 (en) | 1998-04-27 |
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