EP0812304A1 - Verfahren und anlage zur bindung von harz- und teersubstanzen in nasswäscher- und nasselektrofilteranlagen - Google Patents

Verfahren und anlage zur bindung von harz- und teersubstanzen in nasswäscher- und nasselektrofilteranlagen

Info

Publication number
EP0812304A1
EP0812304A1 EP96942167A EP96942167A EP0812304A1 EP 0812304 A1 EP0812304 A1 EP 0812304A1 EP 96942167 A EP96942167 A EP 96942167A EP 96942167 A EP96942167 A EP 96942167A EP 0812304 A1 EP0812304 A1 EP 0812304A1
Authority
EP
European Patent Office
Prior art keywords
wood
wood dust
wet
water
dust
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Withdrawn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
EP96942167A
Other languages
German (de)
English (en)
French (fr)
Inventor
Emil Wieser-Linhart
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.)
BWT Holding GmbH
Original Assignee
BWT AG
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 BWT AG filed Critical BWT AG
Publication of EP0812304A1 publication Critical patent/EP0812304A1/de
Withdrawn legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/286Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D17/00Separation of liquids, not provided for elsewhere, e.g. by thermal diffusion
    • B01D17/02Separation of non-miscible liquids
    • B01D17/0202Separation of non-miscible liquids by ab- or adsorption
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D47/00Separating dispersed particles from gases, air or vapours by liquid as separating agent
    • B01D47/06Spray cleaning
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/18Nature of the water, waste water, sewage or sludge to be treated from the purification of gaseous effluents

Definitions

  • the invention relates to a method for binding emulsified resin and tar substances in the circulating water of wet scrubber and wet electrostatic precipitator systems for waste gas occurring in the wood industry.
  • the raw wood contains a lot of resin (e.g. pine) and is dried at high temperatures (600-800 ° C), besides the cellular water (wood moisture) also a lot of water vapor-volatile resin, tar and fatty acids are stripped out. These substances are still present as gases in the dryer exhaust air at 120 ° C. In the subsequent cooling to the dew point of 50-70 ° C., these substances condense out as aerosols ("blue haze") and can therefore first be deposited as a tar-like coating on the precipitation surfaces of the wet electrostatic precipitator and subsequently washed off with circulating water from there .
  • resin e.g. pine
  • tar and fatty acids are stripped out.
  • the invention aims to provide a method and a plant with which these tar substances are bound by adsorption and can be separated.
  • the method according to the invention has the features that into the circulating water Wood dust is metered, which receives the emulsified substances adsorptively, and in that this wood dust is removed from the water circulation ⁇ removed and sedimented.
  • a wood dust amount of 100-800% of the original raw gas dust load is preferably additionally added.
  • the wood dust is advantageously metered into the exhaust gas fed to the wet washer and wet electrostatic filter system.
  • the sediment obtained can either be recirculated in a dryer or burned with other wood waste in a boiler.
  • the optimum substance for carrying out the method according to the invention was found to be the grinding dust accumulating in large quantities in the chipboard industry. This occurs with surface smoothing in grinding machines. Wood sanding dust has good properties because its affinity for resin and tar is good, whereby the dust turns dark. The sanding dust also has a corresponding fineness and thus a large surface. In addition, the loaded, wetted grinding dust sediments well.
  • the residual product can be disposed of in the form of dewatered sediment either by incineration or in the raw product itself or in a composting facility. It has proven particularly advantageous that a substance is used which corresponds to the natural raw material wood.
  • the grinding dust can be added in the course of the method according to the invention into the raw gas line, into the washer, directly into the circulating water or into the return water line of the sludge discharge device.
  • the wood dust feed device preferably flows into the wetting device of the exhaust gas feed line via a blowing device.
  • the sludge discharge device has a sludge pump and a decanter centrifuge connected downstream thereof, which is connected to the container via a water line.
  • the exhaust gas or the exhaust air of a wood drying system (not shown) in a raw gas line 1 is fed via a prewetting device 2 arranged in this to the lower end of a vertical container 3 of the wet washer and wet electrostatic filter system via an inlet 3 '.
  • the gas flows upward in the container 3 via a washer device 4 and is cooled to the dew point of 60-70 ° C.
  • the condensing aerosols are ionized in a wet electric honeycomb arrangement 5 connected downstream in the flow direction of the gas, to which an electrical high voltage is applied by means of a high voltage unit 6, and are wet ionized in a wet electric filter 7 connected downstream of the honeycomb arrangement 5 or droplet separator.
  • the gas leaves the column 3 at the top through an outlet 3 "as a clean gas.
  • the residues formed in the container 3 are discharged at the lowest container end as sludge via a sludge pump 7 and a decanter centrifuge 8, which is connected to the container 3 via a water pipe 8 ', and deposited as sediment S.
  • the washing water is conveyed up in a circuit, partly via a circuit pump 9 to the scrubber and honeycomb rinse, and partly via a pre-wetting pump 10 to the pre-wetting device 2.
  • a wood dust feed device 11 is provided in the area of the raw gas line 1, which has a wood dust silo 12 with a discharge screw 12 'and a ventilator 13 which sprays the wood dust, preferably wood sanding dust, into the pre-wetting device 1.
  • the wood dust blown into the pre-wetted raw gas is introduced into the container 3 by the raw gas and in this way reaches the washing water circuit.
  • the metering of the wood dust can be regulated according to the respective operating needs via the silo discharge screw 12 '.
  • the exemplary embodiment described can be modified within the scope of the general inventive concept.
  • the wood dust can thus be added directly into the container 3, into the wash water circuit or into the return water line of the sludge discharge device instead of into the raw gas.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Thermal Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Water Supply & Treatment (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Physics & Mathematics (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Separation Of Particles Using Liquids (AREA)
  • Processing Of Solid Wastes (AREA)
  • Electrostatic Separation (AREA)
  • Manufacture Of Macromolecular Shaped Articles (AREA)
  • Adhesives Or Adhesive Processes (AREA)
  • Filtering Materials (AREA)
EP96942167A 1996-01-02 1996-12-12 Verfahren und anlage zur bindung von harz- und teersubstanzen in nasswäscher- und nasselektrofilteranlagen Withdrawn EP0812304A1 (de)

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
AT6/96 1996-01-02
AT0000696A AT402801B (de) 1996-01-02 1996-01-02 Verfahren und anlage zur bindung von harz- und teersubstanzen in nasswäscher- und nasselektrofilteranlagen
PCT/AT1996/000245 WO1997024293A1 (de) 1996-01-02 1996-12-12 Verfahren und anlage zur bindung von harz- und teersubstanzen in nasswäscher- und nasselektrofilteranlagen

Publications (1)

Publication Number Publication Date
EP0812304A1 true EP0812304A1 (de) 1997-12-17

Family

ID=3479124

Family Applications (1)

Application Number Title Priority Date Filing Date
EP96942167A Withdrawn EP0812304A1 (de) 1996-01-02 1996-12-12 Verfahren und anlage zur bindung von harz- und teersubstanzen in nasswäscher- und nasselektrofilteranlagen

Country Status (9)

Country Link
US (2) US5762662A (cs)
EP (1) EP0812304A1 (cs)
AT (1) AT402801B (cs)
AU (1) AU1131897A (cs)
CA (1) CA2214149A1 (cs)
CZ (1) CZ261397A3 (cs)
NO (1) NO973920L (cs)
PL (1) PL322050A1 (cs)
WO (1) WO1997024293A1 (cs)

Families Citing this family (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AT402801B (de) * 1996-01-02 1997-09-25 Bwt Ag Verfahren und anlage zur bindung von harz- und teersubstanzen in nasswäscher- und nasselektrofilteranlagen
US6955733B2 (en) 1997-12-19 2005-10-18 The Procter & Gamble Company Method and system for registering pre-produced webs with variable pitch length
US6444064B1 (en) 1997-12-19 2002-09-03 Procter & Gamble Company Registration system for phasing simultaneously advancing webs of material having variable pitch lengths
US8790444B2 (en) * 2011-03-01 2014-07-29 Rsr Technologies, Inc. Wet electrostatic precipitator and related methods
US8956272B2 (en) * 2011-12-30 2015-02-17 Vanderbeken Ent. Ltd Method and apparatus for removal of tars or resins from a scrubber liquid using a centrifuge with a discharge chamber scraper
US20130168317A1 (en) * 2011-12-30 2013-07-04 Vanderbeken Enterprises Ltd. Dba Drycake Method and apparatus for removal of tars, resins, chars or volatiles from a liquid
CN106068869A (zh) * 2016-07-20 2016-11-09 赵全礼 具有降霾和施肥功能的农业雾化灌溉装置
CN106390654A (zh) * 2016-10-20 2017-02-15 广西金邦泰科技有限公司 一种高效率化工粉料加工过程的除尘器设备
JP2021069993A (ja) * 2019-10-31 2021-05-06 キヤノン株式会社 ウルトラファインバブル生成装置およびその制御方法
CN114100276A (zh) * 2021-12-09 2022-03-01 临澧县宏宝石膏矿业有限公司 一种石膏矿开采除尘设备

Family Cites Families (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2090142A (en) * 1933-12-28 1937-08-17 Ici Ltd Wet purification of gases
DE1519994A1 (de) * 1965-11-10 1969-06-19 Degussa Mittel hoher Absorptionsfaehigkeit zum Binden nicht wasserloeslicher Substanzen
US3928005A (en) * 1974-02-19 1975-12-23 Fuller Co Method and apparatus for treating gaseous pollutants in a gas stream
DE2540691A1 (de) * 1975-09-12 1977-03-17 Hans Adler Ohg Einrichtung zur reinigung von rauchgasen
US4305909A (en) * 1979-10-17 1981-12-15 Peabody Process Systems, Inc. Integrated flue gas processing system
US4431405A (en) * 1982-02-23 1984-02-14 Down River International, Inc. Gas pollution control apparatus and method and wood drying system employing same
US4605640A (en) * 1985-05-29 1986-08-12 The United States Of America As Represented By The Secretary Of Agriculture Oil-absorbent cellulosic derivatives
DE3635461A1 (de) * 1986-10-18 1988-04-28 Bergwerksverband Gmbh Verfahren zur abtrennung von kohlenwasserstoffen aus abwaessern
AT389238B (de) * 1987-08-18 1989-11-10 Simmering Graz Pauker Ag Verfahren zur behandlung der rauchgase und verbrennungsrueckstaende einer verbrennungsanlage, insbesondere abfallverbrennungsanlage
CH676089A5 (cs) * 1988-08-26 1990-12-14 Hydrotechnik Gmbh
DE3914673C3 (de) * 1989-05-03 1994-04-14 Boehler Abfall Abluft Abwasser Verfahren und Vorrichtung zum Reinigen von Abgasen aus Holztrocknungsanlagen
US5614102A (en) * 1990-01-29 1997-03-25 Sakurada; Yasuyuki Method for purifying sewage
AT400725B (de) * 1994-04-11 1996-03-25 Voest Alpine Ind Anlagen Verfahren zum herstellen einer eisenschmelze
JPH08259963A (ja) * 1995-03-20 1996-10-08 Nippon Steel Corp 石炭熱分解ガス中のタールおよびダストの分離方法および装置
AT402801B (de) * 1996-01-02 1997-09-25 Bwt Ag Verfahren und anlage zur bindung von harz- und teersubstanzen in nasswäscher- und nasselektrofilteranlagen

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See references of WO9724293A1 *

Also Published As

Publication number Publication date
CZ261397A3 (cs) 1998-01-14
WO1997024293A1 (de) 1997-07-10
AU1131897A (en) 1997-07-28
AT402801B (de) 1997-09-25
CA2214149A1 (en) 1997-07-10
NO973920D0 (no) 1997-08-26
ATA696A (de) 1997-01-15
US5897689A (en) 1999-04-27
PL322050A1 (en) 1998-01-05
US5762662A (en) 1998-06-09
NO973920L (no) 1997-08-26

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