首页> 外国专利> Working up residues and dust from pyrolysis of spent, recycled domestic batteries includes adding hydrogen peroxide solution to water used for scrubber pyrolysis waste gas containing mercury and compounds

Working up residues and dust from pyrolysis of spent, recycled domestic batteries includes adding hydrogen peroxide solution to water used for scrubber pyrolysis waste gas containing mercury and compounds

机译:处理废旧回收家用电池的热解过程中产生的残留物和粉尘包括将过氧化氢溶液添加到用于洗涤器热解废气中的水(含汞和化合物)中

摘要

In working up residues and dust from pyrolysis of spent, recycled domestic batteries, in which mercury and mercury compounds, in pyrolysis waste gas preferably are absorbed in water in a scrubber fitted with inclined clarifier and tower for reducing mercury (II) with tin (II) chloride, as described in AT 40P 201, hydrogen peroxide solution is added, to eliminate precipitate, sludge etc. Process for working up residues/dust (I) from thermal or pyrolytic treatment of spent, recycled domestic batteries, especially zinc (Zn)/carbon and alkali/manganese (Mn) batteries, involves separating environmentally harmful and/or re-usable metals, especially iron (Fe), Zn and Mn, and wet chemical precipitation of mercury (Hg). (I) contain reaction products of the metals/compounds, especially Zn, Fe, Mn, with pyrolysis gases, e.g. hydrogen chloride, and atmospheric oxygen. After separating a magnetic coarse fraction containing especially Fe and crushing and/or grinding and suspending in water, (I) are treated with hydrochloric acid at pH 1-3, without releasing any gas, especially hydrogen, and subjected to wet oxidation with Mn (III,IV) oxide to convert metallic Fe and Zn and the Mn (III,IV) oxide into the corresponding 3- or 2-valent salts and bring them into solution. Then aqueous caustic alkali, especially sodium hydroxide solution is added in stages to adjust the solution to (1) pH 3.4-4 to precipitate Fe as Fe (III) hydroxide; (2) pH 5-6 to precipitate Zn as Zn hydroxide, preferably 95-98% pure; and (3) pH 6.5-8, with introduction of oxygen, especially air, to precipitate Mn as Mn (III,IV) hydroxide(s), preferably 95-98% pure. Each precipitate is separated in turn. Hg and its compounds, especially Hg (II) chloride, present in the waste gases from pyrolysis are absorbed in a scrubber, preferably in water in a scrubber fitted with an inclined clarifier for separating the slurry from the waste liquor and a reduction tower for reducing Hg(II) with Sn(II) chloride, as described in AT 40P 201. The novelty is that to eliminate, especially dissolve, precipitates, sludge etc. present or formed in the water from the scrubber or to free it from sludge, hydrogen peroxide solution is added in the sludge separator or water flowing through this, preferably in the inclined clarifier. An Independent claim is also included for the plant used in this process.
机译:在处理废旧的回收家用电池的热解过程中产生的残留物和粉尘时,热解废气中的汞和汞化合物最好在装有倾斜澄清器和塔的洗涤器中吸收,该洗涤器配有塔,用于用锡(II)还原汞(II) ),如AT 40P 201中所述,添加过氧化氢溶液以消除沉淀物,污泥等。处理废旧回收家用电池,特别是锌(Zn)的热处理或热解产生的残留物/粉尘(I)的过程/碳和碱/锰(Mn)电池涉及分离对环境有害和/或可重复使用的金属,尤其是铁(Fe),Zn和Mn,以及湿法化学沉淀的汞(Hg)。 (I)包含金属/化合物,特别是Zn,Fe,Mn与热解气体,例如H 2 O的反应产物。氯化氢和大气中的氧气。分离出特别是含有Fe的磁性粗级分并粉碎和/或研磨并悬浮在水中后,将(I)用pH 1-3的盐酸处理,不释放任何气体,尤其是氢气,并用Mn进行湿式氧化( III,IV)氧化物将金属Fe和Zn以及Mn(III,IV)氧化物转化为相应的3价或2价盐并将其溶解。然后分阶段加入苛性碱水溶液,特别是氢氧化钠溶液,以调节溶液至(1)pH 3.4-4,以沉淀出Fe,成为Fe(III)氢氧化物; (2)pH为5-6时,以氢氧化锌的形式沉淀出Zn,最好是纯度为95-98%; (3)pH 6.5-8,引入氧气,尤其是空气,以沉淀出Mn,为Mn(III,IV)氢氧化物,优选95-98%的纯净度。每种沉淀物依次分离。热解废气中存在的Hg及其化合物,尤其是Hg(II)氯化物在洗涤器中吸收,优选在洗涤器中的水中吸收,该洗涤器配有倾斜的澄清池,用于从废液中分离浆液和还原塔,用于还原Hg(II)和氯化Sn(II),如AT 40P 201中所述。新颖之处在于,它可以消除,特别是溶解来自洗涤塔的水中存在或形成的沉淀物,淤渣等,或使其摆脱淤渣,氢将过氧化物溶液添加到污泥分离器中,或者将水流过该污泥分离器,最好是在倾斜的澄清池中。该过程中使用的工厂也包含独立索赔。

著录项

  • 公开/公告号AT410494B

    专利类型

  • 公开/公告日2003-05-26

    原文格式PDF

  • 申请/专利权人 WEBER MARIA DIPL.ING.;

    申请/专利号AT20010001029

  • 发明设计人 WEBER MARIA DIPL.ING.;

    申请日2001-07-03

  • 分类号H01M6/52;

  • 国家 AT

  • 入库时间 2022-08-21 23:59:37

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