TW200914377A - Process & apparatus - Google Patents

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TW200914377A
TW200914377A TW97121968A TW97121968A TW200914377A TW 200914377 A TW200914377 A TW 200914377A TW 97121968 A TW97121968 A TW 97121968A TW 97121968 A TW97121968 A TW 97121968A TW 200914377 A TW200914377 A TW 200914377A
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arsenic
liquid
electrolysis
reference electrode
conductive salt
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TW97121968A
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Chinese (zh)
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Gerard Gasser
Eugenia Yves Santa
Markus Hasenboehler
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Buss Chemtech Ag
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    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B7/00Halogens; Halogen acids
    • C01B7/19Fluorine; Hydrogen fluoride
    • C01B7/191Hydrogen fluoride
    • C01B7/195Separation; Purification
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    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B25/00Phosphorus; Compounds thereof
    • C01B25/16Oxyacids of phosphorus; Salts thereof
    • C01B25/18Phosphoric acid
    • C01B25/234Purification; Stabilisation; Concentration
    • C01B25/237Selective elimination of impurities
    • C01B25/238Cationic impurities, e.g. arsenic compounds
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    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B33/00Silicon; Compounds thereof
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    • C01B33/103Fluosilicic acid; Salts thereof
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    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4676Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electroreduction
    • C02F1/4678Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electroreduction of metals
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    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B3/00Extraction of metal compounds from ores or concentrates by wet processes
    • C22B3/20Treatment or purification of solutions, e.g. obtained by leaching
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    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B30/00Obtaining antimony, arsenic or bismuth
    • C22B30/04Obtaining arsenic
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    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • C22B7/006Wet processes
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    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
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    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
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    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/103Arsenic compounds
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    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/46Apparatus for electrochemical processes
    • C02F2201/461Electrolysis apparatus
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    • C02F2201/461Electrolysis apparatus
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    • C02F2201/46145Fluid flow
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    • C02F2201/46Apparatus for electrochemical processes
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    • C02F2201/461Electrolysis apparatus
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    • C02F2201/46Apparatus for electrochemical processes
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    • C02F2209/02Temperature
    • 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
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    • Y02P10/20Recycling

Abstract

A process for reducing arsenic in an acidic liquid comprising arsenic in an oxidized form, wherein the liquid is subjected to electrolysis in a single step and in a single compartment electrolytic cell using pulsed current in the presence of a conduction salt. A reference electrode comprising an electrolyte bridge made of PTFE is also discussed.

Description

200914377 九、發明說明: 【發明所屬之技術領域】 本發明係關於一種用於砷之去除、回收或者去除且回收 的方法及裝置。更特定言之,本發明係關於一種用於自工 業廢水、天然水及其他液體去除、回收或者去除且回收石申 的方法及裝置。更特定言之,本發明係關於一種用於自氫 氟酸去除、回收或者去除且回收砷的方法。 【先前技術】 無水策化虱一般係藉由氟石及硫酸之混合物反應而產 生。反應中產生的雜質包括四乾化碎、二氧化硫、非揮發 性酸諸如H2S〇4及H3P〇4、水以及砷。期望產物氟化氫習知 地藉由蒸餾而純化。然而’蒸餾方法並不能使砷被分離, 使得產物無水氟化氫仍含有不可接受量的石申。 藉由習知方法製得的無水氟化氫一般含有自大約20至大 約600 ppm的砷’視氟石礦中所含有的砷而定。由於無水 氟化氫在有機及無機化學品的生產中被用作氟化劑,砷 (其係一觸媒毒)的存在可影響其中使用了氟化氫之方法的 效率,且將導致觸媒壽命縮減。另外,在進料流及/或產 物流中砷之存在可引起製程設備的嚴重腐蝕。 稀氟化氫具有多種用途。舉例而言,其被使用於金屬酸 洗及玻璃钮刻中。雖然坤的存在對此等方法不會有中毒效 應’但神將存在於流出物中且因此必須對廢物流進行昂責 之處理以去除砷。不幸地,已知之處理係昂貴的。 珅除了在氟石中被發現以外,亦存在於磷酸岩中。當碟 132210.doc 200914377 酸岩用硫酸處理以產生磷酸時,砷仍作為—雜質留在產物 構酸中。其後若磷酸將使用於食品中則砷必須被特別去 除。 在構灰石(其為一磷酸岩)轉化成磷酸期間,氟石夕酸 (H^iF6)作為一廢棄產物大量產生。然而,揮發性种產物 諸如AsF3存在於氟矽酸中。由於氟矽酸被用於氟化飲用 水,應瞭解去除砷是必要的。氟矽酸在氫氟酸的生產中亦 被用作一起始材料。 〇 2006年美國引入的水質法規要求水中存在之砷的量為 ppb或者更小。在引入此等法規之前,允許存在於水中之 最大砷量係50 ppb。因此將砷從天然或工業水中去除之要 求係極為急切且變得更有甚之。 因此應瞭解,期望提供一種可將砷從可能含有其之任何 液體回收及/或去除的方法。此等液體包括(但不限於广氫 氟酸;氟矽酸諸如H2SiF6及HSiF5 ;磷酸諸如h3P〇4 ;來自 Q 諸如地下水、河水及雨水之任何來源的水;來自堆積場及 礦井的浸析液;以及所有公共及工業流出物。 多種方法已被提出以用於從水、特別是將用作飲用水之 水或從工業流出物去除钟。 該等已知方法可被劃分為物理方法、化學方法、生物方 法及電化方法。 物理方括;|膜方法諸如奈米過滤、逆滲透、電透析 以及吸附方法。吸附方法包括使用活性象土或離子交換樹 月旨的方法。雖然此等方法在-定程度上可去除石t,但其等 132210.doc 200914377 全部具有產生_羞!>4 V" J3A、— 母性液體流出物之缺點,該毒性液體流出 物在丟棄之前必須被處理。關於這一點,請注意在丟棄之 前珅廢物應被中和及穩定。即使在此種處理之後,丢棄也 .、、毒f廢物之專屬堆積場中進行。此等方法及後續丢棄 之成本很高。 化學方法包括其中利用例如氧、臭氧、氣、氣、次氣酸 -、過猛酸鹽、芬頓(FentGn)試劑或過氧化氫作為氧化劑 Γ200914377 IX. INSTRUCTIONS OF THE INVENTION: TECHNICAL FIELD OF THE INVENTION The present invention relates to a method and apparatus for the removal, recovery or removal and recovery of arsenic. More specifically, the present invention relates to a method and apparatus for the removal, recovery or removal of industrial wastewater, natural water and other liquids, and for the recovery of the stone. More specifically, the present invention relates to a process for removing, recovering or removing and recovering arsenic from hydrofluoric acid. [Prior Art] Anhydrous hydrazine is generally produced by a reaction of a mixture of fluorspar and sulfuric acid. Impurities generated in the reaction include tetra-drying, sulfur dioxide, non-volatile acids such as H2S〇4 and H3P〇4, water, and arsenic. It is desirable that the product hydrogen fluoride is purified by distillation. However, the distillation method does not allow the arsenic to be separated so that the product anhydrous hydrogen fluoride still contains an unacceptable amount of schist. The anhydrous hydrogen fluoride produced by the conventional method generally contains arsenic contained in the arsenic fluorite ore from about 20 to about 600 ppm. Since anhydrous hydrogen fluoride is used as a fluorinating agent in the production of organic and inorganic chemicals, the presence of arsenic, which is a catalytic agent, can affect the efficiency of the process in which hydrogen fluoride is used and will result in reduced catalyst life. In addition, the presence of arsenic in the feed stream and/or the production stream can cause severe corrosion of the process equipment. Dilute hydrogen fluoride has many uses. For example, it is used in metal pickling and glass button engraving. Although the existence of Kun does not have a poisoning effect on these methods, 'God will exist in the effluent and therefore must deal with the waste stream to remove arsenic. Unfortunately, the treatments known are expensive. In addition to being found in fluorite, it is also present in phosphate rock. When the disk 132210.doc 200914377 acid rock is treated with sulfuric acid to produce phosphoric acid, arsenic remains as an impurity in the product acid. Thereafter, if phosphoric acid is used in foods, arsenic must be specifically removed. Fluorite (H^iF6) is produced in large quantities as a waste product during the conversion of the limestone, which is a rock of the monophosphate, to phosphoric acid. However, volatile species such as AsF3 are present in fluoroantimonic acid. Since fluoroantimonic acid is used in fluorinated drinking water, it is important to understand that arsenic removal is necessary. Fluorine acid is also used as a starting material in the production of hydrofluoric acid.水质 Water quality regulations introduced in the United States in 2006 require arsenic in water to be ppb or less. The maximum amount of arsenic present in the water is allowed to be 50 ppb prior to the introduction of these regulations. Therefore, the requirement to remove arsenic from natural or industrial water is extremely urgent and more desirable. It will therefore be appreciated that it would be desirable to provide a method for recovering and/or removing arsenic from any liquid that may contain it. Such liquids include, but are not limited to, polyhydrofluoric acid; fluoroantimonic acids such as H2SiF6 and HSiF5; phosphoric acids such as h3P〇4; water from any source such as groundwater, river water and rainwater; leachate from accumulation yards and mines And all public and industrial effluents. A variety of methods have been proposed for the removal of clocks from water, especially water used as drinking water or from industrial effluents. These known methods can be divided into physical methods, chemistry Methods, biological methods, and electrochemical methods. Physical methods; | Membrane methods such as nanofiltration, reverse osmosis, electrodialysis, and adsorption methods. Adsorption methods include methods using active image soil or ion exchange trees, although such methods are - Stones can be removed to some extent, but their 132210.doc 200914377 all have the disadvantage of producing _ shame! > 4 V" J3A, a maternal liquid effluent that must be disposed of before disposal. In this regard, please note that the waste should be neutralized and stabilized before disposal. Even after such treatment, it is carried out in the exclusive accumulation yard of the waste. High cost, and the like comprising discarding the subsequent chemical wherein using, for example, oxygen, ozone, air, gas, acid gas time -, too much salt, Fenton (FentGn) reagent or hydrogen peroxide as oxidizing agent Γ

L 、:/、物理方法一樣,此等具有留下毒性廢物之缺 點,為了安全丢棄該等毒性廢物而必須進行處理。此外’ 若此等化學方法被使用於與無水氟化氣的生產組合中,則 在下游需要對產物傲i隹—,κ ^ 進步蒸館。替代方法包括與鐵或鋁 的共沉澱。此等方法亦產生毒性廢物。 舉㈠而。生物方法包含使用微生物混合劑(cocktail)對 2的生物處理。此等微生物—般係特定生長且當被使用時 =澱毒性化合物諸如珅。此等生物方法之主要缺點係其 生毒性於邊,為了安全丢棄該毒性齡潰而必須進行處 理。生物方法之另一缺點係其等不可使用於酸性環境中。 用於去除奴已知電化方法包切三㈣ 五價坤AS(Vp在待處理之組 )為 高濃酸之情況下,使用—炫鹽導電L具有極低導電性之 咖觀9她51_39描述了心自無 ::化雜#諸如畔的電化方法。此方法使用一電解槽二 能之”及屬力水氟化氫處於液體狀 度及c力下㈣。在電解期間’存在於氣化氫中之 I32210.doc 200914377 雜質被氧化。特定言之,_被氧化為仍保持在溶液中的一 非揮發性形式。此方法之一缺點係需蒸館無水氣化氣及產 生一必須處理或小心丟棄之毒性液體廢物。 由於無水氟化氫具有極低導電性,在直流電將用於該方 *之情況中’ us测別及仍51_9教示應存在—電解 質諸如氟化鉀或其他鹼金屬氟化物或者水。在任何情況 . τ ’直流電條件下的電解效率差且產率低,除非添加電解 質鹽或水。 雖然假若使用一交流電該方法將更有效,但會發生氟損 失且蒸餾殘渣含有氟化氫及氟化砷化合物諸如HAsF6。此 殘渣必須在毒性廢物之特定堆積場中被穩定化並丟棄。 一替代方法描述於EP 〇48〇254中。此處描述了 一種方 去其中…、水氟化氫藉由施加假定為直流電之電流而受到 電解。反應係在一情性氣體氛圍中進行以防止潛在爆炸氣 體的累積。此方法的缺點是,需要對不僅含有氧化物且對 U 纟有砷之廢氣亦須進行複雜且昂貴的洗滌。反應需要應用 一高達50 V之電壓。因此反應的電力消耗極高使得該方法 相對昂貴。此外,由於使用一高電壓及由於該方法必須運 #相當長的-段時間,故存在—風險即無錢化氫將分解 為H2及F2,其將最終導致氟化物損失。與其他方法一樣, 亦有毒性液體及氣體流出物之共產生問題,該等毒性液體 及氣體流出物在丟棄之前必須進行處理。 US 55"437描述—電化方法,其中使用了一自0.5至 H)〇〇 Hz,較佳地在1〇與1〇〇 Hz之間的脈衝電流以及— 132210.doc 200914377 观或更少,較佳地㈣與5G%之間的工作循環。該方法 適用於含有電活性化學物種諸如金屬離子之溶液。陰極經 組態成使得其具有一大的表面積。 ^ ^極係由直彳生為1 mm或 比一表面積為80至1500 m2/g^_貞4 g之*粒子填充床製成。陰極且 有一至少大約10,000之粗糙因數 、 双丘了選擇地塗佈有一離子 父換樹脂諸如全氟績酸離子鐘抵+ 卞鍵樹知。沉積的金屬為銅、 銀、金、鋅、鎳、汞、鉛、鈾、锃 鈾鎬和鉻。然而,由於其高 氧化電位,該方法不適用於;^。卜 _ . 八L, :/, physical methods, these have the disadvantage of leaving toxic waste, which must be disposed of in order to safely discard such toxic waste. In addition, if these chemical methods are used in combination with the production of anhydrous fluorinated gases, the products need to be proud of the downstream, κ ^ progressive steaming. Alternative methods include co-precipitation with iron or aluminum. These methods also produce toxic waste. Give (a) instead. The biological method involves the biological treatment of 2 with a microbial cocktail. Such microorganisms are generally growth-specific and when used = toxic compounds such as hydrazine. The main disadvantage of these biological methods is their toxicity to the side, which must be treated in order to safely discard the toxic age. Another disadvantage of biological methods is that they cannot be used in an acidic environment. For the removal of slaves known to electrification method package cut three (four) Wu price Kun AS (Vp in the group to be treated) is high concentration of acid, the use of - Hyun salt conductive L has very low conductivity of the coffee view 9 she 51_39 description The heart is self-existing::Chemical# such as the electrochemical method of the shore. This method uses an electrolytic cell and a hydrogenated hydrogen fluoride under liquidity and c force (4). During the electrolysis, I32210.doc 200914377 impurities are oxidized in the hydrogenated hydrogen. In particular, _ Oxidation to a non-volatile form that remains in solution. One of the disadvantages of this method is the need to steam the anhydrous gasification gas and produce a toxic liquid waste that must be disposed of or carefully discarded. Because anhydrous hydrogen fluoride has very low conductivity, DC will be used in the case of the party * 'measuring and still 51_9 teaches should exist - electrolytes such as potassium fluoride or other alkali metal fluorides or water. In any case. τ 'DC electrolysis efficiency is poor and produced The rate is low unless electrolyte salt or water is added. Although this method will be more effective if an alternating current is used, fluorine loss will occur and the distillation residue contains hydrogen fluoride and arsenic fluoride compounds such as HAsF6. This residue must be in a specific accumulation field of toxic waste. Stabilized and discarded. An alternative method is described in EP 〇 48〇 254. A method is described here..., water fluoride is applied by applying It is electrolyzed for the current of direct current. The reaction is carried out in an inert atmosphere to prevent the accumulation of potentially explosive gases. The disadvantage of this method is that it is necessary to complicate the exhaust gas containing not only oxide but also arsenic. And expensive washing. The reaction requires the application of a voltage of up to 50 V. Therefore, the power consumption of the reaction is extremely high, making the method relatively expensive. Moreover, due to the use of a high voltage and because the method must be carried out for a relatively long period of time, Presence—the risk that no hydrogen will be decomposed into H2 and F2, which will eventually lead to fluoride loss. As with other methods, there are also problems with the co-production of toxic liquids and gaseous effluents. Must be processed before disposal. US 55 " 437 describes - electrochemical method, which uses a pulse current from 0.5 to H) 〇〇 Hz, preferably between 1 〇 and 1 〇〇 Hz and - 132210.doc 200914377 View or less, preferably a duty cycle between (4) and 5G%. This method is suitable for solutions containing electroactive chemical species such as metal ions. The cathode is configured to It has a large surface area. ^ ^ The pole is made of 1 mm or a packed bed of particles with a surface area of 80 to 1500 m2 / g ^ _ 4 g. The cathode has at least about 10,000 The roughness factor and the double hills are selectively coated with an ion-parent resin such as a perfluorinated acid ion clock ring + 卞 bond tree. The deposited metals are copper, silver, gold, zinc, nickel, mercury, lead, uranium, thorium uranium And chromium. However, due to its high oxidation potential, this method is not suitable for; ^. Bu_.

Ύ 此外,該方法不可用於高 度濃縮酸介質中。 因此所有已知方法均需要制附加試劑使得產生了必須 進行處理或進行小心丟棄之廢物流。甚至是基於氧化之電 化方法亦留下必須被處理之毒性廢物。 因此期望提供-種方法能以沒有任何殘留毒性廢物需被 處理之方式將石申自液體去除。特定言之,期望提供一種方 法’在該方法中_以金屬形式被回收,因為其係隨後可被 用於多種工業中的一商業產品。 【發明内容】 因此根據本發明,提供了一種用於還原包含氧化形式之 砷之酸性液體中的砷之方法,其中該液體於一傳導鹽存在 之情況下使用脈衝電流在一單隔間電解槽中受到單步電 解0 所謂"酸性",意指液體具有0至8的一1)11值(酸鹼值)。 因此,被處理之液體中的任何As(III)將根據下列反應被 還原: 132210.doc -10· 200914377Ύ In addition, this method is not suitable for use in highly concentrated acid media. Therefore, all known methods require the preparation of additional reagents to produce a waste stream that must be disposed of or carefully discarded. Even oxidatively based electrochemical methods leave toxic waste that must be disposed of. It is therefore desirable to provide a method for removing the stone from the liquid in a manner that does not require any residual toxic waste to be treated. In particular, it is desirable to provide a method in which it is recycled in a metal form as it can then be used in a commercial product in a variety of industries. SUMMARY OF THE INVENTION Accordingly, in accordance with the present invention, there is provided a method for reducing arsenic in an acidic liquid comprising arsenic in an oxidized form, wherein the liquid is pulsed in a single compartment cell in the presence of a conductive salt It is subjected to single-step electrolysis. The so-called "acid" means that the liquid has a 1)11 value (pH value) of 0 to 8. Therefore, any As(III) in the treated liquid will be reduced according to the following reaction: 132210.doc -10· 200914377

As(III) + 3 e_ |As 當其後將被進一步還原為上述之As金屬時,存在於被處 理之液體中的任何As(V)將被還原為As(III),但此全部係 作為一單步反應。傳導鹽亦作為使陽極去極化之作用,且 此最小化或較佳地防止陽極之任何As(III)至As(V)的再氧 化。 因此’在本發明之方法中,氧化還原系統之平衡有利於As(III) + 3 e_ |As When it is later reduced to the above As metal, any As(V) present in the treated liquid will be reduced to As(III), but this is all A single step reaction. The conductive salt also acts to depolarize the anode, and this minimizes or preferably prevents reoxidation of any As(III) to As(V) of the anode. Therefore, in the method of the present invention, the balance of the redox system is favorable

置換熱力學最不穩定之物種As金屬。類似地,該方法有利 於最慢之反應,即還原,而非動力學最快之反應。 應瞭解本發明之一優點係由於砷被還原為金屬狀態故其 可被輕易隔離及回收。此狀態下之砷係可再循環以適於工 業用途的一商業產品。此種用途包括掺雜於微電子工業 中。回收及隨後使用砷之能力意味著本發明之方法特具經 濟吸引力。 本發明之另一優點係,除了期望的砷金屬,沒有產生必 須被安全地處理或丟棄之廢物。 本發明之方法可適用於去除被處理之液體中任何濃度的 砷,諸如從數十百分比例如2〇%至微量例如兆分之幾。液 體本身可係導電的。然而,由於傳導鹽的存在,具有低或 極低導電性電位之液體可進行本發明之方法。 在本發明之—較佳態樣中,該方法係在一參考電極存在 下進行。 。與標準氫電極(NHE)相 V之氧化還原電位的傳導鹽 任何適當之傳導鹽可被使用 較,具有大約0.6 V至大約-1.8 132210.doc 200914377 最佳適*的鹽包括過氧化氳和肼衍生物產品,諸如氟化 肼、N2H4F、硫酸肼、硝酸肼、磷酸肼及氫氧化肼,其中 氟化骄最佳。 般而<=*,肼鹽被選擇為使得其適於被處理之介質且不 留下任何附加雜質。因此被處理之物質為氤化氫時氟化肼 係理心的,對於H3P〇4磷酸肼係理想的,對於H2S〇4硫酸肼 係理心的’等等。在不受任何理論限制之情況下,據信傳 導鹽會增加電解將發生於其巾之介質的導電性。根據波貝 克斯(Pourbaix)圖,對於將氧化還原電位維持在穩 定區,增加介質之導電性係重要的。 另卜傳導鹽亦作為使陽極去極化之作用,從而防止陽 極有意外氧化反應發生。 可歸於傳導鹽之另一優點係其不會以雜質污染溶液,且 不會產生液體或氣體毒性廢物。這是因為傳導鹽在電解期 間被消耗且因此在操作結束時從液體消失。較佳地,本發 明之反應提供既無毒性也不是非預期之產物。因此,該方 法不會引起釋放至環境中之毒性物質。舉例而言,當 2 為傳導鹽時解產物將為揮發性之氮以及仍保持 於反應混合物中之I化氫,其中被處理之液體係氟化氣。 任何適當量之傳導鹽可被添加至被處理之液體中。在— ^佳配置中’添加之傳導鹽的量係按照其在電解反應結束 時將被完全消耗之數量進行劑量投配。傳導鹽一般可降解 且不會在液體中留下需進一步純化之污染物。 施加至槽之電流係脈衝電流。在不受任何理論限制之情 132210.doc •12- 200914377 況下,應瞭解強酸通常係良好之電導體。然而,氯氣酸為 弱酸,即其具有低的解離常數且因此其在高濃度下具有極 低之導電性。 雖然先前技術方法中的—些建議使用脈衝電流,但此等 先前技術方法中石申之還原的效率差。關於這一點,請注意 在電化沉積中石申係所有金屬中最慢之金屬。然而,在本發 明中’由於傳導鹽亦發揮绅氧化抑制劑之作用,傳導鹽的 存在克服了先前技術方法的若干缺點。因此使用脈衝電流 γ有效地實現本發明之方法。脈衝電流可係正弦、方形或 二角形’其中方形最佳。電流可以為對稱或非對稱。在一 較佳配置中,使用一負的非對稱電流。 可使用任何適當之電流。電流頻率可自0至大約2_ 版,其中大約細他區域内之頻率最佳。工作循環,亦 稱為循環比,可在〇及嶋之間變化,但較佳地為大約5〇 至大約75%。 1 一本發明之方法可用於處理含有石申之任何液體。然而,在 一實例巾,包切之液射能為㈣氫。氫可為未稀 ==任何濃度存在於水溶液中。在使用未稀釋的 舍-:及兄下,電解將在使得說化氫處於液體狀態之適 田/皿度及壓力下進行。 含=:=於處理氟石夕酸、磷酸(包括其多種形式),及 "文、酸混合物、酸性或中性流出物。 β亥方法可以—連、續或批式製程實現。 、電解之•度被選擇以最適於進行之電解。適當之溫 132210.doc -13· 200914377 度l括自大約-60C及大約1 〇(TC之間的溫度。最佳溫度為 自大約7°C至大約i4°c。 系統之溫度可藉由任何適當的方法來控制。在一配置 中’溫度可藉由-冷卻液體之循環而控制。在電解槽具有 :雙層殼之情況下,冷卻液體—般在雙層殼内之空間中揭 環。其-般還被用於控制儲存容器中及至一廢氣冷凝器的 液體。Replace the As metal of the most unstable thermodynamic species. Similarly, this method facilitates the slowest reaction, i.e., reduction, rather than the fastest kinetic reaction. It will be appreciated that one of the advantages of the present invention is that it can be easily isolated and recovered due to the reduction of arsenic to a metallic state. The arsenic in this state can be recycled as a commercial product suitable for industrial use. Such uses include doping in the microelectronics industry. The ability to recover and subsequently use arsenic means that the process of the present invention is particularly economically attractive. Another advantage of the present invention is that, in addition to the desired arsenic metal, no waste that must be safely disposed of or discarded is produced. The method of the present invention can be adapted to remove any concentration of arsenic in the liquid being treated, such as from tens of percent, e.g., 2% to traces, such as parts per trillion. The liquid itself can be electrically conductive. However, a liquid having a low or very low conductivity potential can be subjected to the method of the present invention due to the presence of a conductive salt. In a preferred embodiment of the invention, the method is carried out in the presence of a reference electrode. . Conductive salts of the redox potential of the standard hydrogen electrode (NHE) phase V. Any suitable conductive salt can be used, having a purity of from about 0.6 V to about -1.8 132210.doc 200914377 The most suitable salts include barium peroxide and barium. Derivative products such as barium fluoride, N2H4F, barium sulfate, barium nitrate, barium phosphate and barium hydroxide, of which fluorination is the best. Typically, <=*, the phosphonium salt is selected such that it is suitable for the medium being treated without leaving any additional impurities. Therefore, the substance to be treated is fluorinated with hydrogen fluoride, and is ideal for H3P〇4 lanthanum phosphate, and for H2S〇4 barium sulfate. Without being bound by any theory, it is believed that the conductance of the salt will increase the conductivity of the medium from which the electrolysis will occur. According to the Pourbaix diagram, it is important to increase the conductivity of the medium in order to maintain the oxidation-reduction potential in the stable region. In addition, the conductive salt acts as a depolarizing anode to prevent accidental oxidation of the anode. Another advantage attributed to the conductive salt is that it does not contaminate the solution with impurities and does not produce liquid or gaseous toxic waste. This is because the conductive salt is consumed during electrolysis and thus disappears from the liquid at the end of the operation. Preferably, the reactions of the present invention provide products that are neither toxic nor unexpected. Therefore, this method does not cause toxic substances released into the environment. For example, when 2 is a conductive salt, the product will be volatile nitrogen and hydrogenated hydrogen remaining in the reaction mixture, wherein the liquid system being treated is fluorinated. Any suitable amount of conductive salt can be added to the liquid being treated. The amount of conductive salt added in the -good configuration is dosed according to the amount that will be completely consumed at the end of the electrolysis reaction. Conductive salts are generally degradable and do not leave contaminants in the liquid that require further purification. The current applied to the tank is a pulse current. Without being bound by any theory 132210.doc •12- 200914377, it should be understood that strong acids are usually good electrical conductors. However, the chlorine acid is a weak acid, i.e., it has a low dissociation constant and thus it has extremely low conductivity at a high concentration. While some of the prior art methods suggest the use of pulsed currents, the efficiency of the reduction by Shishen in these prior art methods is poor. In this regard, please note that the slowest metal of all metals in the Shishen system in electrochemical deposition. However, in the present invention, the presence of a conductive salt overcomes several disadvantages of the prior art methods because the conductive salt also functions as a ruthenium oxidation inhibitor. The method of the present invention is thus effectively implemented using pulse current γ. The pulse current can be sinusoidal, square or digonal. The current can be symmetrical or asymmetrical. In a preferred configuration, a negative asymmetrical current is used. Any suitable current can be used. The current frequency can range from 0 to about 2_, where the frequency is approximately the best in the fine area. The duty cycle, also known as the cycle ratio, can vary between 〇 and 嶋, but is preferably from about 5 至 to about 75%. 1 A method of the invention can be used to treat any liquid containing shishen. However, in an example towel, the liquid energy of the package cut is (iv) hydrogen. Hydrogen can be undiluted == any concentration present in the aqueous solution. Under the use of undiluted house-: and brother, the electrolysis will be carried out under conditions and pressures that allow the hydrogen to be in a liquid state. Contains =: = in the treatment of fluorite, acid (including its various forms), and " text, acid mixture, acidic or neutral effluent. The β-hai method can be implemented in a continuous, continuous or batch process. The degree of electrolysis is selected to be the most suitable for electrolysis. The appropriate temperature 132210.doc -13· 200914377 degrees l is from about -60 C and about 1 〇 (temperature between TC. The optimum temperature is from about 7 ° C to about i 4 ° C. The temperature of the system can be used by any A suitable method is used to control. In one configuration, the temperature can be controlled by the circulation of the cooling liquid. In the case where the electrolytic cell has a double-layered shell, the cooling liquid is generally uncovered in the space inside the double-shell. It is also typically used to control the liquid in the storage vessel and to the exhaust gas condenser.

方法可在任何適當裝置中進行。電解槽可由任何適 當之材料製成,只要其可抵抗被處理之組合物。適當之材 料包括塑膠,諸如氟聚合物,例如聚偏二氣乙稀、聚四氣 乙締及其類似物。替代之適當材料包括金屬諸如錄、錯、 銀、鉑、不銹鋼、鎳合金、鉻及其組合。 於八中可進仃電解之槽可為任何適當組態。舉例而言, 其可為圓筒形、平行六面體、螺旋形或是—管束。。 適於本發明之方法中传 成。適-材… 自任何適當之材料製 :=㈣包括不錢鋼、錄、金、鋼或碳。此等可被翠 5、且口使用。在使用碳之情況下 ^ U- JO. 為其多種开)式中 石二Γ♦例而言’其可為其玻璃質形式的石墨、全剛 =寶石及其類似物。在-配置中,陽極可為一碳= 且陰極可由不録铜艰士 電極 伴1 , 、 /成。不銹鋼陰極可藉由金屬石申之沉穑 保護。此具有防止溶液受污染之優 旧 微電子工業中使用之超純氣化氨:::法被用於從 尤為重要。 11甲去除碎之情況下,這點 亦可使用一參考雷掹 ^ ^ 考電極。參考電極可由任何適當之材料製 I32210.doc 200914377 身又由適以耐受腐蚀性溶液之材料製成。 四氟乙烯或其他氟聚合物。 成。然而,其— 適當之材料係聚 參考電極一船且古 叙/、有一穩定且固定之電位及因此允許調整 :制::沉積期間隨著改變之離子濃度而改變的陰極電 t極的存在可使電位_直保持在形成As金屬 圍内,日4古H , 夂 在波貝克斯(Pourbaix)圖中列出的。應 解,坤還原為氣體純3係不被期望的。 應瞭The method can be carried out in any suitable device. The electrolytic cell can be made of any suitable material as long as it is resistant to the composition being treated. Suitable materials include plastics such as fluoropolymers such as polyvinylidene chloride, polytetramethylene and the like. Suitable alternative materials include metals such as phono, mis, silver, platinum, stainless steel, nickel alloys, chromium, and combinations thereof. The tank that can be used for electrolysis in the eighth can be configured as appropriate. For example, it can be cylindrical, parallelepiped, spiral or tube bundle. . It is suitable for propagation in the process of the invention. Appropriate material... Made from any suitable material: = (4) Includes no money for steel, gold, steel or carbon. These can be used by Cui. In the case of the use of carbon ^ U-JO. For its various formulas, it can be its glassy form of graphite, all-gear = gemstone and the like. In the -configuration, the anode can be a carbon = and the cathode can be accompanied by a copper-free electrode with 1 , / /. The stainless steel cathode can be protected by metal stone. This is an ultra-pure vaporized ammonia used in the microelectronics industry to prevent contamination of the solution: the :: method is especially important. In the case where the nail is removed, this can also be used with a reference Thunder ^ ^ test electrode. The reference electrode can be made of any suitable material, I32210.doc 200914377, and made of a material suitable for tolerating corrosive solutions. Tetrafluoroethylene or other fluoropolymer. to make. However, the appropriate material is a reference electrode that is a ship and has a stable and fixed potential and thus allows for adjustment: the presence of a cathodic electrical t-pole that changes with the altered ion concentration during deposition. Keep the potential_ straight in the formation of As metal, the day 4 ancient H, 夂 listed in the Pourbaix diagram. It should be understood that the reduction of Kun into a gas pure 3 system is not expected. Should

電極可為任何適當之組態。舉例而言,其等可為平板, ,者其等可為包括圓筒形、管狀或螺旋形之另一組態。無 响為哪種組態,電極可以為多孔的或無孔的。另外,電極 可由球形離子形成。 裝置可包括—脈衝產生器。產生器提供允許工作循環之 ^換的矩形形式之非對稱脈衝。如上所示,可使用任何適 tj >考電極。傳統型參考電極由一可稱為坩堝之陶瓷膜 製成。該膜發揮-電解質橋之作用。“,由於大部分陶 竞材料含有Si〇2’其等不可抵抗氫氟酸。另外,大部分材 料會受到氫氟酸侵钱,且將發生受氫氟酸之污染。為克服 此等難點,已提供了一種經改良之參考電極。 机因此’根據本發明之-第二態樣,提供了一具有一新賴 设計之參考電極,該新穎設計允許對電化槽的極精細控制 且克服了上文細述之難點。 在本發明之第二態樣的一較佳實施例中,參考電極包含 一由PTFE製成的電解f橋。該橋可包括—由脚!_生 產的結膜,或者可抵抗酸性環境諸域化氫的任何多孔材 132210.doc 15 200914377 料。適虽之抵抗材料包括藍寶石或Ti〇2。naf腿係杜邦 (DuPont)的商標。 本發月之上述第一態樣之方法中使用本發明之此第二態 樣的參考電極可使電化槽獲得精細控制。 槽之大小及電極的間距將被熟知本技藝者選擇為適於被 處理之液體。然而’ -般而言’電極之間的距離在大約 0.1 mm至大約1000 mm之區域内。 待處理之液體一般被泵抽穿過電解槽。泵可為一薄膜 泵。速度一般被選擇為與電極之砷的還原速度相容。可使 用任何適當的速度的速度包括請_之範圍 内的速度。更特定言之,速度可在_之範圍内。The electrodes can be of any suitable configuration. For example, they may be flat plates, and the like may be another configuration including a cylindrical shape, a tubular shape, or a spiral shape. For no configuration, the electrodes can be porous or non-porous. In addition, the electrodes may be formed of spherical ions. The device can include a pulse generator. The generator provides an asymmetric pulse in the form of a rectangle that allows the commutation of the duty cycle. As indicated above, any suitable tj > test electrode can be used. The conventional reference electrode is made of a ceramic film which can be called tantalum. This membrane acts as an electrolyte bridge. "As most of the Tao Jing materials contain Si〇2', they are not resistant to hydrofluoric acid. In addition, most of the materials will be invaded by hydrofluoric acid and will be contaminated by hydrofluoric acid. To overcome these difficulties, An improved reference electrode has been provided. Thus, in accordance with the second aspect of the present invention, a reference electrode having a new design is provided which allows for extremely fine control of the electrochemical cell and overcomes In a preferred embodiment of the second aspect of the invention, the reference electrode comprises an electrolytic f-bridge made of PTFE. The bridge may comprise a conjunctiva produced by the foot! Any porous material that is resistant to hydrogenation in the acidic environment 132210.doc 15 200914377. Suitable resistance materials include sapphire or Ti〇2. The naf leg is a trademark of DuPont. The first aspect of this month The use of the second embodiment of the reference electrode of the present invention allows fine control of the electrochemical cell. The size of the trench and the pitch of the electrodes will be well known to those skilled in the art as being suitable for the liquid being processed. However, 'electrode The distance between them is in the range of about 0.1 mm to about 1000 mm. The liquid to be treated is generally pumped through the electrolytic cell. The pump can be a thin film pump. The speed is generally chosen to be compatible with the reduction rate of the arsenic of the electrode. Speeds that can be used at any suitable speed include speeds within the range of _. In particular, speeds can be within _.

陰極之電㈣被設定及控制以允料離子還原為金屬狀 態。對於一酸性介質,可使用範圍在大約+0·3至大約_〇·6 VANHE之範圍内的電位,其中刪係標準氫電極。對於一 中性介質,可使用範圍在大約_0.24至大約_丨v/nhe之範 圍内的電位。適於可使用之任何鹼性介質的一適當電位可 自波貝克斯(P〇urbaix)圖計算出。任何情況下,電位 設定為避免砷的形成’係由於砷係一極具毒性氣體之故。 如上所不’可使用一參考電極。電位之控制將使用三個 電極來完成。操作電位的測量將在參考電極及陰極之間進 打。陰極電位的調整可藉由增加或減少陰極與陽極之間之 電位差異Δυ而進行。在此模式下,陽極發揮輔助電極之 作用 旦達到砷的離子電位’則藉由將電流維持為當達到正 132210.doc -16- 200914377 * 確還原電位時一開始所測定之相同電流,製程被改變為恒 電流全等導航模式(Aamperostaticspiloting m〇de)。首先, 在批式操作中,電極沉積在一常數電壓下進行,其為恒電 位操作,直到達到介質的擴散極限。此可藉由電流的減少 Z觀察到。為克服濃度極限’其後電壓增加而電流保持為 常數,其即上文提及之恒電流操作。 本發明之方法可在一情,改氣體諸如4下進彳以避免滿 度凝結。 已確認的是,本發明之方法可被整合為其他生產機具的 部刀或者,其可被提供為一行動部件以適於單一或暫 時之操作。 經由舉例,現將參考若干附圖來描述本發明。 【實施方式】 本發明之電化方法可在其中進行之電解槽丨被繪示於圖i 中。槽1包括一適用賴極的鍍金板及一適用作陰極的銅 板槽1藉纟聚四^乙稀管而連接至一雙壁電解質儲存器 2,在該雙壁電解質儲存器2中一致冷液在一受控溫度下循 環。一參考電極3浸潰於該電解質儲存器中。 一氟聚合物薄膜泵4在該槽及儲存器之間以迴路循環待 純化之電解質。 一惰性沖洗氣體,諸如氮,被吹至错存器内之電解質表 面。鼠在排出至-抽吸罩之前流過一冷_器5及一鹼性吸 收塔。槽1被放置在一冷卻容器内以便維持其溫度。 一可調整之脈衝電流電源產生器6被連接在一 A3電極全 132210.doc -17· 該等實例不應被The cathode (4) is set and controlled to allow the ions to be reduced to a metallic state. For an acidic medium, a potential in the range of from about +0. 3 to about _〇·6 VANHE can be used, with a standard hydrogen electrode being deleted. For a neutral medium, a potential in the range of about _0.24 to about _丨v/nhe can be used. An appropriate potential for any alkaline medium that can be used can be calculated from the P〇urbaix plot. In any case, the potential is set to avoid the formation of arsenic because of the extremely toxic gas of arsenic. A reference electrode can be used as described above. The potential control will be done using three electrodes. The measurement of the operating potential will be made between the reference electrode and the cathode. The adjustment of the cathode potential can be carried out by increasing or decreasing the potential difference Δυ between the cathode and the anode. In this mode, the anode acts as the auxiliary electrode and reaches the ionic potential of arsenic. By maintaining the current to the same current as when the positive potential is reached, 132210.doc -16- 200914377 * Change to the constant current full navigation mode (Aamperostaticspiloting m〇de). First, in batch operation, electrode deposition is performed at a constant voltage that operates at a constant potential until the diffusion limit of the medium is reached. This can be observed by the reduction in current Z. To overcome the concentration limit, the voltage is then increased and the current remains constant, which is the constant current operation mentioned above. The method of the present invention allows for the incorporation of a gas such as 4 to avoid full condensation. It has been confirmed that the method of the present invention can be integrated into a knife of another production implement or it can be provided as a mobile component for single or temporary operation. The invention will now be described, by way of example, with reference to certain drawings. [Embodiment] The electrolytic cell in which the electrochemical method of the present invention can be carried out is shown in Fig. i. The tank 1 comprises a gold plate suitable for the pole and a copper plate tank 1 suitable for the cathode, which is connected to a double wall electrolyte reservoir 2 by means of a polysilicon tube, in which the liquid is uniformly cooled. Circulate at a controlled temperature. A reference electrode 3 is immersed in the electrolyte reservoir. The fluoropolymer film pump 4 circulates the electrolyte to be purified in a loop between the tank and the reservoir. An inert flushing gas, such as nitrogen, is blown onto the electrolyte surface in the trap. The mouse flows through a colder 5 and an alkaline absorber before being discharged to the suction hood. The tank 1 is placed in a cooling vessel to maintain its temperature. An adjustable pulse current power generator 6 is connected to an A3 electrode. 132210.doc -17· These examples should not be

200914377 等機構(A3 electrode setups)内。一奎供4± 考電極蜂^_7錢接於參 之間,且一安培計8被連接於電路中。 P著電解的進行,還原之砷部分沉 U rr^ L, 只仕,合液中或在電極 成一沉積物。其後砷可藉由任何適 μ, 田之方法而去除。 虽之方法包括分離技術諸如過濾。 ’ 現將參考以下實例來說明本發明方法 視為限制。 實例1及2 執行使用交流電之U二次運轉。在每—次運轉中, 配備有鍍金不銹鋼陽極及一銅陰極的電解槽以一 12丨/m比 之速率循環有大約400 g的無水氟化氫。陽極及陰極之表n 面積為0.5 dm2。該等電極被設定為使得其等被分開大約2 mm ° 對於每一次運轉測定砷雜質之各自起始濃度。傳導鹽 被添加至溶液。第一次運轉之槽的溫度為7至1)1, 而第二次運轉之槽的溫度為9至14。(:。交流電之電壓使用 一電源產生器來調整’且允許電流持續運轉表1中列出之 時間。頻率被設定為200 kHz且循環比為75%。操作模式為 恒電流。 此處進行並分析了液體的一樣本。與各自運轉的電解還 原之前之分析及電解還原後之液體分析相對應的資料列於 表1 〇 132210.doc -18- 200914377 運轉 丨時間(h) |交流電壓 溫度。C 開始時As ppm 結束時As ppm 1轉化率 % 1 72 1.3-9.1 ^7-12 106 「2.5 98 2 30 2.2-4 9-14 144 4 97 增加運轉時間將增加轉化率。在—替代配置中,運轉時 間可藉由使用較大表面積之電極而減少。 【圖式簡單說明】In 200914377 and other institutions (A3 electrode setups). One quintal for 4± test electrode bee ^_7 money is connected between the parameters, and an ammeter 8 is connected to the circuit. P is carried out by electrolysis, and the reduced arsenic partially sinks U rr ^ L, which is only in the liquid or in the electrode to form a deposit. Subsequent arsenic can be removed by any suitable method. Although methods include separation techniques such as filtration. The method of the present invention will now be described with reference to the following examples as a limitation. Examples 1 and 2 perform U secondary operation using AC power. In each operation, an electrolyzer equipped with a gold-plated stainless steel anode and a copper cathode was circulated with about 400 g of anhydrous hydrogen fluoride at a rate of 12 丨/m. The surface area of the anode and cathode is 0.5 dm2. The electrodes were set such that they were separated by approximately 2 mm ° for each run to determine the respective starting concentrations of arsenic impurities. Conductive salts are added to the solution. The temperature of the first run tank is 7 to 1)1, and the temperature of the second run tank is 9 to 14. (: The voltage of the AC is adjusted using a power generator' and allows the current to continue to run for the time listed in Table 1. The frequency is set to 200 kHz and the cycle ratio is 75%. The operating mode is constant current. The same data of the liquid was analyzed. The data corresponding to the analysis before the respective electrolytic reduction and the liquid analysis after the electrolytic reduction are listed in Table 1 〇132210.doc -18- 200914377 Operation time (h) | AC voltage temperature. As ppm begins at the end of As ppm As ppm 1 conversion % 1 72 1.3-9.1 ^7-12 106 "2.5 98 2 30 2.2-4 9-14 144 4 97 Increasing the run time will increase the conversion rate. In the - alternative configuration The running time can be reduced by using a larger surface area electrode.

圖1係適於本發明之一適當電化槽的圖式;及 圖2係根據本發明之第二態樣的一參考電極。 【主要元件符號說明】 1 電解槽 2 雙壁電解質儲存器 3 參考電極 4 薄膜泵 5 冷凝器 6 脈衝電流電源產生器 7 毫伏特計 8 安培計 132210.doc •19-BRIEF DESCRIPTION OF THE DRAWINGS Figure 1 is a drawing suitable for a suitable electrolysis cell of the present invention; and Figure 2 is a reference electrode in accordance with a second aspect of the present invention. [Main component symbol description] 1 Electrolyzer 2 Double-wall electrolyte reservoir 3 Reference electrode 4 Membrane pump 5 Condenser 6 Pulse current power generator 7 millivoltmeter 8 ammeter 132210.doc •19-

Claims (1)

200914377 十、申請專利範圍: 1’ -種用於還原包含氧化形式之砷之酸性液體中的砷之方 法’其中該液體於-傳導鹽存在下使用脈衝電流在 隔間電解槽中進行單步驟電解。 2·如叫求項1之方法,其中該傳導鹽為氟化肼、硫酸肼、 ‘ 硝酸肼、氫氧化耕或過氧化氫。 3.如請求項2之方法,其中該傳導鹽是氟化肼。 4. 如請求項1至3中任一項之方法,其中該傳導鹽以—使得 f) 其在電解結束時被完全消耗之量添加。 5. 如„青求項!至3中任一項之方法,其中該傳導鹽被降解且 不會污染該液體。 6. 如咕求項1之方法,其中該電流頻率係自〇至大約 kHz。 7. 如咕求項6之方法’其中該電流頻率為大約kHz。 8. 如明求項丨至3中任一項之方法,其中一工作循環係自〇 至 100〇/〇。 9. 如睛求項8之方法,其中該工作循環係自大約50至大約 75%。 1〇·如請求項丨至3中任一項之方法,其中含有砷之該液體為 氣化氫、氟矽酸或磷酸。 11 ·如印求項〗至3中任一項之方法其中該電解係在大約_6〇 °c至大約1 〇〇。(:之溫度下進行。 12,如印求項方法’其中該電解係在大約7。匸至大約 °c之溫度下進行。 132210.doc 200914377 13. 如請求項1至3中任一項之方法,其中使用一參考電極。 14. 一種參考電極,其包含一由PTFE製成的電解質橋。 15. 如請求項14之參考電極,其中該橋包括一由NAFION、 藍寶石或者Ti02製得的結膜。200914377 X. Patent application scope: 1 'A method for reducing arsenic in an acidic liquid containing an oxidized form of arsenic' wherein the liquid is subjected to a single-step electrolysis in a compartment electrolyzer using a pulsed current in the presence of a conducting salt . 2. The method of claim 1, wherein the conductive salt is barium fluoride, barium sulfate, strontium nitrate, hydrogen peroxide or hydrogen peroxide. 3. The method of claim 2, wherein the conductive salt is cesium fluoride. 4. The method of any one of claims 1 to 3, wherein the conductive salt is added in an amount such that f) is completely consumed at the end of electrolysis. 5. The method of any one of 3, wherein the conductive salt is degraded and does not contaminate the liquid. 6. The method of claim 1, wherein the current frequency is from about kHz to about kHz 7. The method of claim 6, wherein the current frequency is about kHz. 8. The method of any one of the preceding claims, wherein one of the duty cycles is from 100 〇 to 〇. The method of claim 8, wherein the working cycle is from about 50 to about 75%. The method of any one of claims 3 to 3, wherein the liquid containing arsenic is hydrogenated hydrogen or fluoroquinone The method of any one of the above-mentioned items, wherein the electrolysis system is carried out at a temperature of from about -6 〇 ° c to about 1 〇〇 (: at a temperature of 12.) The method of any one of claims 1 to 3, wherein a reference electrode is used, wherein a reference electrode is used, wherein the electrolysis system is carried out at a temperature of from about 7. It comprises an electrolyte bridge made of PTFE. 15. The reference electrode of claim 14, wherein the bridge comprises a by NAFION Ti02 prepared sapphire or conjunctiva. 132210.doc -2-132210.doc -2-
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