EP2366036A1 - Recovery of metals and acids from exhausted pickling solutions and/or neutralization sludge - Google Patents

Recovery of metals and acids from exhausted pickling solutions and/or neutralization sludge

Info

Publication number
EP2366036A1
EP2366036A1 EP20090767938 EP09767938A EP2366036A1 EP 2366036 A1 EP2366036 A1 EP 2366036A1 EP 20090767938 EP20090767938 EP 20090767938 EP 09767938 A EP09767938 A EP 09767938A EP 2366036 A1 EP2366036 A1 EP 2366036A1
Authority
EP
European Patent Office
Prior art keywords
nickel
sludge
neutralization
chromium
solution
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.)
Withdrawn
Application number
EP20090767938
Other languages
German (de)
English (en)
French (fr)
Inventor
Marco Zavattoni
Olga Piva
Roberto Caimi
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.)
Reorbis Holding Bv
Original Assignee
Condoroil Impianti SRL
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 Condoroil Impianti SRL filed Critical Condoroil Impianti SRL
Publication of EP2366036A1 publication Critical patent/EP2366036A1/en
Withdrawn legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • 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
    • C22B7/007Wet processes by acid leaching
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B17/00Sulfur; Compounds thereof
    • C01B17/69Sulfur trioxide; Sulfuric acid
    • C01B17/90Separation; Purification
    • C01B17/901Recovery from spent acids containing metallic ions, e.g. hydrolysis acids, pickling acids
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • 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
    • C01B7/196Separation; Purification by distillation
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G37/00Compounds of chromium
    • C01G37/02Oxides or hydrates thereof
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G37/00Compounds of chromium
    • C01G37/08Chromium sulfates
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G49/00Compounds of iron
    • C01G49/02Oxides; Hydroxides
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G49/00Compounds of iron
    • C01G49/14Sulfates
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G53/00Compounds of nickel
    • C01G53/04Oxides; Hydroxides
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G53/00Compounds of nickel
    • C01G53/10Sulfates
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B23/00Obtaining nickel or cobalt
    • C22B23/04Obtaining nickel or cobalt by wet processes
    • C22B23/0453Treatment or purification of solutions, e.g. obtained by leaching
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B23/00Obtaining nickel or cobalt
    • C22B23/04Obtaining nickel or cobalt by wet processes
    • C22B23/0453Treatment or purification of solutions, e.g. obtained by leaching
    • C22B23/0461Treatment or purification of solutions, e.g. obtained by leaching by chemical methods
    • CCHEMISTRY; METALLURGY
    • 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
    • C22B3/04Extraction of metal compounds from ores or concentrates by wet processes by leaching
    • C22B3/06Extraction of metal compounds from ores or concentrates by wet processes by leaching in inorganic acid solutions, e.g. with acids generated in situ; in inorganic salt solutions other than ammonium salt solutions
    • C22B3/08Sulfuric acid, other sulfurated acids or salts thereof
    • CCHEMISTRY; METALLURGY
    • 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
    • CCHEMISTRY; METALLURGY
    • 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
    • C22B3/44Treatment or purification of solutions, e.g. obtained by leaching by chemical processes
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B34/00Obtaining refractory metals
    • C22B34/30Obtaining chromium, molybdenum or tungsten
    • C22B34/32Obtaining chromium
    • CCHEMISTRY; METALLURGY
    • C23COATING 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
    • C23GCLEANING OR DE-GREASING OF METALLIC MATERIAL BY CHEMICAL METHODS OTHER THAN ELECTROLYSIS
    • C23G1/00Cleaning or pickling metallic material with solutions or molten salts
    • C23G1/36Regeneration of waste pickling liquors
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2006/00Physical properties of inorganic compounds
    • C01P2006/80Compositional purity
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Definitions

  • the present invention relates to the recovery of metals and acids coming from exhausted pickling solutions and/or neutralization sludge of stainless steel in their total separation into secondary raw materials that can be reused, such as refractory oxides, iron sulphates and hydroxides, chromium hydroxide or metallic chromium or chromates, metallic nickel and hydrofluoric, nitric and/or sulphuric acids.
  • secondary raw materials such as refractory oxides, iron sulphates and hydroxides, chromium hydroxide or metallic chromium or chromates, metallic nickel and hydrofluoric, nitric and/or sulphuric acids.
  • the discharged bath portion is generally neutralized with kmewash for obtaining a sludge comprising metals, mainly iron, chromium and nickel in the form of hydroxides and anions, fluorides and sulphates in the form of calcium salts.
  • a sludge comprising metals, mainly iron, chromium and nickel in the form of hydroxides and anions, fluorides and sulphates in the form of calcium salts.
  • the object of the present invention is a process of treating and recovering almost all the components of pickling waste, allowing to split it into fully recyclable secondary raw materials, avoiding to forward it to the dump site.
  • the present invention relates also to the treatment of sludge produced by neutralization of waste, even when already stored in a dump site, where it is necessary to provide for a previous redissolution in an acidic medium as disclosed hereinafter.
  • the first stage of the process firstly provides for the separation of the insoluble oxides included in waste, through a decantation, washing and compaction unit. These oxides may be reused in the smelting furnace. By the same unit it is also possible to recover the oxides lost in the quenching section and in the rinsing steps after pickling.
  • the pickling solution after oxide separation, is forwarded to a distillation unit where it is brought to boiling after addition of a suitable quantity of 98% sulphuric acid.
  • volatile acids such as nitric or hydrofluoric acid
  • hydrofluoric acid is obtained industrially by attack of sulphuric acid on fluorite.
  • Nitric acid too at a higher concentration than the azeotropic one, is produced by distillation in presence of sulphuric acid.
  • sulphuric acid moves nitric and hydrofluoric acids from their salts and complexes, reforming the free acids allowing their almost complete distillation.
  • the distilled nitric and hydrofluoric acids are condensed and forwarded to the work tanks or storage.
  • the clear solution essentially comprising high concentration sulphuric acid, part of chromium and nickel sulphates and traces of iron sulphates is added with 98% sulphuric acid until the acid concentration required by the process is restored, and then is forwarded to the evaporator in place of fresh sulphuric acid to treat another pickling solution.
  • the precipitated salts are rinsed with an aqueous solution of sulphuric acid of suitable concentration. This treatment causes the redissolution of the precipitated nickel and chromium salts while iron sulphate remains undissolved and may be recovered.
  • the acidic solution containing chromium and nickel and iron traces is forwarded to a first neutralization stage, after oxidation of divalent to trivalent iron, if required.
  • the clear solution and the sludge rinsing waters are additionally neutralized up to pH 8-9, i.e. to complete nickel precipitation.
  • the precipitated hydroxide is then dewatered by microfiltration, filter pressing or other suitable means.
  • neutralization is conducted eidier with sodium hydroxide or hmewash.
  • Nickel hydroxide may be further treated until metal in its elementary form is obtained.
  • the hydroxide is taken to a dissolution equipment kept at pH controlled by sulphuric acid. Dissolution pH is kept at about 3.5-4.5, so that nickel hydroxide goes in solution as sulphate, while the possible traces of iron and chromium hydroxides due to incomplete precipitation during the first neutralization, as well as calcium sulphate present when limewash is used in the second neutralization, remain undissolved.
  • the sludge coming from microfiltration or filter pressing after neutralization with sodium hydroxide, essentially consists of nickel hydroxide that is totally dissolved in sulphuric acid leaving only a litde residue.
  • sludge from filter press after neutralization with limewash, leaves a heavy residue of calcium sulphate.
  • this precipitate is heavy and compact, so that it may be separated from the clear solution of nickel sulphate in a quick and complete manner by simple settling.
  • As the sludge coming from filter press contain less water than sludge from microfiltration, after dissolution they produce solutions which have more nickel, thus easier to be treated by electrodeposition.
  • the nickel sulphate solution is then fed to the cathode area of an electrodialysis cell, where nickel in metal form is deposited on the cathode.
  • the working conditions are such that the deposit is dendritic and can be easily removed by stripping plates passing near the cathode at fixed times.
  • the metal stripped from the electrode in the form of pellets is collected in a suitable container at the cell bottom. After filtering and rinsing steps, these nickel pellets may be recovered directly in the steelworks.
  • this acid When this acid reaches a fixed concentration, it is discharged to be recovered in the above described stage of hydroxide dissolution.
  • Use of a membrane cell was preferred in place of an undivided cell, as it allows to avoid the anodic oxidation of the chromium ion, traces of which are possibly present in the solution of nickel sulphate, into chromate and to keep low the acid concentration at the cathode, so as to have always a very high faradic yield.
  • the addition of some components like chelating and buffer agents in the sulphate solution allows to optimize the faradic yield.
  • a further integration of the disclosed process concerns the separation of chromium from iron in the first produced hydroxide sludge, this separation being possible because of the amphoteric behaviour of chromium, having a trend to return in solution at strongly alkaline pHs, as shown in the Pourbaix diagram illustrated in the figure of the annexed drawing.
  • the sludge precipitated at a pH between 3.5 and 4.5 after settling, rinsing and removal of the clear solution, is further alkalized with sodium hydroxide up to pH 10, thus redissolving chromium hydroxide. After removal of the clear solution, the undissolved iron hydroxide is rinsed and again filter pressed.
  • the alkaline solution of trivalent chromium, combined with the sludge rinsing water, may be again neutralized up to pH 7.5-8 where trivalent chromium is again fully precipitated in the form of hydroxide or the solution may again undergo electrochemical reduction to obtain chromium in metal state or even undergo oxidation to obtain a chromate solution. If one decides to use this technique for sludge produced by neutralization of pickling baths already stored in authorized dump sites, it is necessary to add to the process a preliminary passage of dissolving sludge in an acid.
  • the sulphuric solution containing the metal salts initially present in the sludge follows step by step the process above described for the exhausted pickling baths.
  • the insoluble fraction before going to the settling, rinsing and compacting stage as hereinbefore described must be treated with hydrochloric acid so as to dissolve calcium sulphate contained in the fraction.
  • the obtained acidic solution of calcium salts after neutralization and drying steps may be used as road antifreeze.
  • a pickling bath solution of the following composition is used: Iron (III) 22 g/1
  • Nitrates 55 g/1 To 1 1 of this solution an equal volume of 98% sulphuric acid is added. Distillation is conducted at atmospheric pressure for 5 hr, up to constant volume. Boiling temperature attains 12O 0 C. At the end of distillation the concentrated solution is placed in a IMOF cone to determine the existing liquid fraction. Details are as follows:
  • the clear fraction has the following composition indicated as percentage on the total of each component initially present:
  • Example 1 The experiment illustrated in Example 1 was repeated as described. However the solid fraction was not redissolved in water but underwent consecutive extractions with a solution of 1 % sulphuric acid. This treatment causes the total redissolution of nickel and chromium salts, leaving undissolved the iron salts. The obtained sulphuric solution contains as percentage:
  • the salty fraction of the concentrate of a distillation test after dissolution in a solution of 1% sulphuric acid, has the following composition: Iron (III) 0.05 g/1
  • the first neutralization phase at pH between 3.5 and 4.5 was conducted either with IN sodium hydroxide or 10% limewash. The obtained results are shown in the following tables.
  • the sludge was dissolved in nitromuriatic acid and the sample was analyzed obtaining the following results.
  • the sludge was dissolved in nitromuriatic acid and the sample was analyzed obtaining the following results
  • the obtained solution has the following composition Nickel (II) 12 g/1
  • EXAMPLE 6 A steelworks sludge coming from a storage dump site and having a dry contents of

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Inorganic Chemistry (AREA)
  • Metallurgy (AREA)
  • Materials Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Manufacturing & Machinery (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Treatment Of Sludge (AREA)
EP20090767938 2008-11-06 2009-11-02 Recovery of metals and acids from exhausted pickling solutions and/or neutralization sludge Withdrawn EP2366036A1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
ITVA2008A000056A IT1393792B1 (it) 2008-11-06 2008-11-06 Recupero di metalli e acidi da soluzioni esauste di decapaggio e/o da fanghi di neutralizzazione
PCT/EP2009/007925 WO2010051992A1 (en) 2008-11-06 2009-11-02 Recovery of metals and acids from exhausted pickling solutions and/or neutralization sludge

Publications (1)

Publication Number Publication Date
EP2366036A1 true EP2366036A1 (en) 2011-09-21

Family

ID=41066280

Family Applications (1)

Application Number Title Priority Date Filing Date
EP20090767938 Withdrawn EP2366036A1 (en) 2008-11-06 2009-11-02 Recovery of metals and acids from exhausted pickling solutions and/or neutralization sludge

Country Status (3)

Country Link
EP (1) EP2366036A1 (it)
IT (1) IT1393792B1 (it)
WO (1) WO2010051992A1 (it)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113881857A (zh) * 2021-09-09 2022-01-04 云南云铜锌业股份有限公司 一种湿法锌冶炼镉回收工序产出的含钴溶液的处理方法

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FI127664B (en) 2017-10-20 2018-11-30 Crisolteq Ltd Process for recovery of components from a pickle acid regeneration residue
CN107881518B (zh) * 2017-11-20 2019-07-19 安徽新洲钢业有限公司 一种钢管生产车间的污泥处理线
CN107893235B (zh) * 2017-11-20 2019-08-09 安徽新洲钢业有限公司 一种钢管生产车间的污泥处理方法
CN109536711B (zh) * 2018-11-06 2024-01-16 泰州华昊废金属综合利用有限公司 金属表面处理废物的资源化利用处理系统
WO2021105215A1 (en) 2019-11-28 2021-06-03 Scanacon Ab Metal recovery method
CN111020187A (zh) * 2019-12-10 2020-04-17 广东邦普循环科技有限公司 氢氧化镍的制备方法
FI129345B (en) 2019-12-19 2021-12-15 Crisolteq Ltd A method for treating a pickling acid regeneration precipitate

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FI58519C (fi) * 1978-12-07 1981-02-10 Rosenlew Ab Oy W Foerfarande foer regenerering av betningssyror
FI81127C (fi) * 1988-04-18 1990-09-10 Outokumpu Oy Foerfarande foer regenerering av betsyror vid zinkgalvaniseringsprocesser.
US5500098A (en) * 1993-08-05 1996-03-19 Eco-Tec Limited Process for regeneration of volatile acids
JPH0860388A (ja) * 1994-08-12 1996-03-05 Nippon Yakin Kogyo Co Ltd 硝弗酸系ステンレス酸洗浴用濾過器および濾過方法

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See references of WO2010051992A1 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113881857A (zh) * 2021-09-09 2022-01-04 云南云铜锌业股份有限公司 一种湿法锌冶炼镉回收工序产出的含钴溶液的处理方法

Also Published As

Publication number Publication date
IT1393792B1 (it) 2012-05-08
WO2010051992A1 (en) 2010-05-14
ITVA20080056A1 (it) 2010-05-07

Similar Documents

Publication Publication Date Title
EP2366036A1 (en) Recovery of metals and acids from exhausted pickling solutions and/or neutralization sludge
CN109850928B (zh) 从酸洗残余物中回收组分的方法
CN105256141B (zh) 一种电镀污泥资源化处理及综合回收利用的方法
CN104641018B (zh) 用于从金属盐溶液中产生或回收盐酸的方法和设备
CN101717868B (zh) 从含铟镓蒸馏废酸中综合回收铟镓方法
CN100473617C (zh) 锌电解冲洗废水循环利用的处理方法
CN104609683B (zh) 一种铬鞣污泥中重金属铬的再生方法
WO2020196046A1 (ja) ニッケルおよびコバルトを含有する水酸化物からのニッケルおよびコバルト含有溶液の製造方法
Diban et al. Zinc recovery and waste sludge minimization from chromium passivation baths
KR101021180B1 (ko) 고순도 황산 코발트 제조방법
CA2492183C (en) Method and device for recycling metal pickling baths
CN111304444B (zh) 一种含铬污泥中分离回收铜、铁、锌、镍、铬的处理方法
US20100278686A1 (en) Process for recovering metals and metal compounds from mined ore and other metal-bearing raw source materials
CN102388168B (zh) 用于沉淀阳离子金属氢氧化物以及从酸性溶液中回收硫酸的方法和装置
CN109321745A (zh) 利用金属表面处理废物制备镍板的方法
CN109576494B (zh) 利用金属表面处理废物制备硫酸钠的方法
JP3831805B2 (ja) 石油系燃焼灰の処理方法
CN104402145B (zh) 利用含亚铁盐废水制备氢氧化铁的生产方法
CN108996752B (zh) 一种从镍的萃余废水中回收低浓度镍的方法
CN112758899B (zh) 一种废硫酸溶液的回收利用方法
JP2001179214A (ja) 石油系燃焼灰の処理方法
DE19520441C2 (de) Verfahren zur hydrometallurgischen Aufarbeitung und Verwertung von Reststoffen und Abfällen
CN116751985A (zh) 一种从铅锌冶炼废水中综合回收锌的方法
UA147980U (uk) Спосіб рекупераційної утилізації гальванічних шламів
JP2004027280A (ja) リン酸塩化成処理スラッジのリサイクル方法

Legal Events

Date Code Title Description
PUAI Public reference made under article 153(3) epc to a published international application that has entered the european phase

Free format text: ORIGINAL CODE: 0009012

17P Request for examination filed

Effective date: 20110606

AK Designated contracting states

Kind code of ref document: A1

Designated state(s): AT BE BG CH CY CZ DE DK EE ES FI FR GB GR HR HU IE IS IT LI LT LU LV MC MK MT NL NO PL PT RO SE SI SK SM TR

RAP1 Party data changed (applicant data changed or rights of an application transferred)

Owner name: REORBIS HOLDING B.V.

DAX Request for extension of the european patent (deleted)
STAA Information on the status of an ep patent application or granted ep patent

Free format text: STATUS: THE APPLICATION IS DEEMED TO BE WITHDRAWN

18D Application deemed to be withdrawn

Effective date: 20150602