EP1542934A2 - Procede de traitement d eaux residuaires par bio-reacteur a membranes - Google Patents

Procede de traitement d eaux residuaires par bio-reacteur a membranes

Info

Publication number
EP1542934A2
EP1542934A2 EP03798216A EP03798216A EP1542934A2 EP 1542934 A2 EP1542934 A2 EP 1542934A2 EP 03798216 A EP03798216 A EP 03798216A EP 03798216 A EP03798216 A EP 03798216A EP 1542934 A2 EP1542934 A2 EP 1542934A2
Authority
EP
European Patent Office
Prior art keywords
sludge
polyelectrolyte
liquid effluent
biological
effluent
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Withdrawn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
EP03798216A
Other languages
German (de)
English (en)
French (fr)
Inventor
Chrystelle Langlais
Michel Cordier
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.)
Suez International SAS
Original Assignee
Degremont SA
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 Degremont SA filed Critical Degremont SA
Publication of EP1542934A2 publication Critical patent/EP1542934A2/fr
Withdrawn legal-status Critical Current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
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/14Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
    • C02F11/147Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents using organic substances
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D65/00Accessories or auxiliary operations, in general, for separation processes or apparatus using semi-permeable membranes
    • B01D65/02Membrane cleaning or sterilisation ; Membrane regeneration
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D65/00Accessories or auxiliary operations, in general, for separation processes or apparatus using semi-permeable membranes
    • B01D65/08Prevention of membrane fouling or of concentration polarisation
    • 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
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/444Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/12Activated sludge processes
    • C02F3/1236Particular type of activated sludge installations
    • C02F3/1268Membrane bioreactor systems
    • C02F3/1273Submerged membrane bioreactors
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Definitions

  • the present invention relates to the treatment of waste water using membrane bio-reactors.
  • the daily flow rate at the top that is to say liquid effluent from the dehydration operation, represents commonly 1 to 5% of the daily wastewater supply rate urban and sometimes more than 10% of the daily flow when it comes to treating industrial wastewater.
  • This option can manage the risk of clogging of the membranes of the bio-reactor, but it does not eliminate the risk of an accidental overdose of polyelectrolytes during the treatment of sludge. Controlling such a risk is all the more difficult to ensure since the quantitative analysis of the residuals of the polyelectrolytes contained in the head returns is today technically complex, even impossible. b) By subjecting the effluents from the sludge dewatering treatment to a pre-treatment in order to destroy the residual quantities of polyelectrolytes.
  • the present invention has therefore set itself the objective of allowing the recycling, at the head of the water sector of a wastewater treatment installation by membrane bio-reactors, of the effluent originating from the sludge sector, ie that is to say the step of dewatering excess sludge from the water industry, completely eliminating the risk of clogging of the membranes of the water industry by residual polyelectrolytes from the mud industry.
  • this invention relates to a process for treating waste water by a membrane bio-reactor comprising a step of dewatering the sludge and recycling, at the top of the bio-reactor, of the liquid effluent from the sludge dewatering, characterized in that:
  • the biological sludges extracted from the bio-reactor are brought into contact with the liquid effluent originating from the sludge dehydration step so that the residual content of said effluent in polyelectrolyte having been used for conditioning the sludges during the dewatering step migrates to biological sludge; the biological sludge is separated from the liquid effluent so as to obtain, on the one hand a liquid effluent free of polyelectrolyte and on the other hand a biological sludge loaded with polyelectrolyte; the liquid effluent free of polyelectrolyte is recycled at the top of the membrane bio-reactor and, - the biological sludge loaded with polyelectrolyte is discharged towards the dehydration stage.
  • the separation of the biological sludge from the liquid effluent is carried out by filtration on icrofiltration or ultrafiltration membranes.
  • the membranes of the sludge system act as a real physical barrier and produce an effluent free of traces of polyelectrolytes which can be recycled on the system. water, that is to say at the head of the bio-reactor, without risk of clogging of the membranes of the latter, the biological sludge or flocs, loaded with polyelectrolytes being discharged towards the sludge dehydration stage.
  • FIG. 1 is a schematic view showing an installation implementing the method according to the present invention and, Figure 2 is a view similar to Figure 1, relating to an example of implementation of the method of the invention.
  • FIG 1 there is shown schematically in 1 the water treatment of urban or industrial waste water, this sector comprising a membrane bio-reactor.
  • This installation includes a workshop for dewatering sludge from the water industry, generally designated by the reference 4, with an injection of polyelectrolyte for the conditioning of sludge, this workshop producing, on the one hand dehydrated sludge and, on the other hand, a dewatering effluent evacuated using a pipe 6.
  • the excess sludge from the water system is brought into contact with the dewatering effluent brought through the pipe 6, in a contactor 2.
  • the residual quantity of polyelectrolyte contained in the dehydration effluent migrates from the liquid phase towards the biological flocs or sludges coming from the water sector, by phenomena of adsorption, absorption and flocculation at levels very far from saturation.
  • the polyelectrolyte fixing yield is close to 100%.
  • the contactor 2 can for example be a fast-mixing reactor "TURBACTOR” as described in the Water Technical Memento, Volume 2, page 638, edited by DEGREMONT (Edition du Cinquantenaire 1989).
  • the separation of the biological mud and the liquid phase is then carried out by filtration so as to obtain a liquid effluent free of polyelectrolyte, recycled at the head of the water sector using a pipe 7 and a biological mud loaded with polyelectrolyte which is brought to the dehydration workshop 4 via line 5.
  • this separation can be carried out by filtration on icrofiltration or ultrafiltration membranes acting as a physical barrier so as to produce an effluent free of traces of polyelectrolyte.
  • This effluent can therefore be recycled on the water sector without risk of clogging of the membranes of this sector.
  • the membranes of the mud sector can have any geometry (flat, tubular, hollow fiber), be made of any suitable material (organic or ceramic) and have any operating configuration (external system or submerged system).
  • Figure 2 illustrates an example of implementation of the method of the invention.
  • the characteristic values of the installation have been mentioned used during this implementation and the data obtained.
  • the area of membranes 3 (60 m 2 ) installed on the sludge sector represents only 3% of the area of membranes (2000 m 2 ) of the water sector bio-reactor.
  • the risk of accidentally clogging the membranes is limited to 3% of the total membrane surface of the treatment installation.
  • the fact of dissociating the membranes of the water industry 1 and the membranes 3 of the mud industry enables chemical washing of the membranes of the mud industry without reducing the filtration capacity of the water industry.
  • the dehydration effluent recycled at the top of the water sector is free of polyelectrolyte, which eliminates any risk of clogging of the membranes of the water sector.
  • the invention makes it possible to reduce the consumption of polyelectrolyte used during the conditioning of the sludge in the workshop. dehydration 4.
  • the dosage of polyelectrolyte necessary for the dewatering of the sludge produced by the water sector is 10 kg / TMeS. Recycling polyelectrolyte “leaks” to the dehydration workshop (line 5) makes it possible to reduce polyelectrolyte consumption by 10%, the latter then being 1.8 kg / d instead of 2 kg / d.
  • the advantages brought by the present invention are in particular the following: - it makes it possible to control the clogging character of the liquid effluents resulting from the sludge dehydration stage by transfer of a small quantity of polyelectrolyte to a large quantity of biological flocs (ratio 500 to 4000); - It guarantees the absence of residual traces of polyelectrolyte in the liquid effluent recycled at the head of the water sector, which eliminates the risk of clogging of the membranes of this sector; - it makes it possible to reduce the dosage of polyelectrolyte during the dewatering of the sludge thanks to the recycling of polyelectrolyte leaks on the sludges coming from the water sector, before their conditioning.

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • General Chemical & Material Sciences (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)
  • Activated Sludge Processes (AREA)
  • Treatment Of Sludge (AREA)
EP03798216A 2002-09-24 2003-09-23 Procede de traitement d eaux residuaires par bio-reacteur a membranes Withdrawn EP1542934A2 (fr)

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
FR0211788A FR2844784B1 (fr) 2002-09-24 2002-09-24 Procede de traitement d'eaux residuaires par bio-reacteur a membranes
FR0211788 2002-09-24
PCT/FR2003/002796 WO2004028986A2 (fr) 2002-09-24 2003-09-23 Procede de traitement d'eaux residuaires par bio-reacteur a membranes

Publications (1)

Publication Number Publication Date
EP1542934A2 true EP1542934A2 (fr) 2005-06-22

Family

ID=31970933

Family Applications (1)

Application Number Title Priority Date Filing Date
EP03798216A Withdrawn EP1542934A2 (fr) 2002-09-24 2003-09-23 Procede de traitement d eaux residuaires par bio-reacteur a membranes

Country Status (19)

Country Link
US (1) US7135115B2 (es)
EP (1) EP1542934A2 (es)
JP (1) JP2006500208A (es)
KR (1) KR20050043986A (es)
CN (1) CN1293001C (es)
AU (1) AU2003276364A1 (es)
BR (1) BR0314842A (es)
CA (1) CA2500135A1 (es)
DE (1) DE03798216T1 (es)
ES (1) ES2239935T1 (es)
FR (1) FR2844784B1 (es)
HK (1) HK1081517A1 (es)
MX (1) MXPA05003269A (es)
NO (1) NO20051991L (es)
PL (1) PL376562A1 (es)
RU (1) RU2321552C2 (es)
TR (1) TR200502228T3 (es)
UA (1) UA80724C2 (es)
WO (1) WO2004028986A2 (es)

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100372784C (zh) * 2006-02-08 2008-03-05 哈尔滨工业大学 污泥外循环复合式膜生物反应器脱氮回收磷污水处理方法
DE102006034984A1 (de) * 2006-07-28 2008-01-31 Universität Kassel Verfahren und Vorrichtung zur biologischen Abwasserreinigung
US7695624B2 (en) * 2008-06-09 2010-04-13 Otv Sa Method and system for treating water and utilizing a membrane filtering system
US8828229B2 (en) * 2010-10-04 2014-09-09 In-Pipe Technology, Inc. Distributed facultative bacteria water treatment system with membrane biological reactor package plant augmentation
US9631170B2 (en) 2011-10-06 2017-04-25 University Of Wyoming Genetically inducible hydrogen peroxide resistance and production
CN102491505A (zh) * 2011-11-20 2012-06-13 江苏鼎泽环境工程有限公司 一种减轻膜生物反应器中膜污染的方法
EP3067324B1 (en) 2015-03-11 2019-09-18 Politechnika Gdanska Method for the preparation of electrodes of boron-doped nanocrystalline diamond
US20170001889A1 (en) * 2015-07-01 2017-01-05 CoResource Solutions, LLC Micro-encapsulating flocculating dispersion water treatment system

Family Cites Families (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US1999973A (en) * 1933-08-21 1935-04-30 Albert L Genter Sewage purification
US5087378A (en) * 1990-05-31 1992-02-11 Pori, International, Inc. Process for enhancing the dewaterability of waste sludge from microbiological digestion
EP0503115A1 (de) * 1991-03-13 1992-09-16 Wehrle-Werk Ag Verfahren und Vorrichtung zur biologischen Reinigung von mit biologisch schwer oder nicht abbaubaren Inhaltsstoffen organisch belasteten Abwässern
DE4401705A1 (de) * 1994-01-21 1995-07-27 Mueller Umwelttechnik Vorrichtung zum Teilentwässern von Rohschlämmen
JP3234710B2 (ja) * 1994-04-01 2001-12-04 株式会社オートセット スラッジ処理装置
EP0979215A1 (en) * 1997-04-30 2000-02-16 Ciba Specialty Chemicals PLC Dewatering of sewage sludge
JP3739188B2 (ja) * 1997-08-08 2006-01-25 株式会社クボタ 膜分離活性汚泥法
US6872312B1 (en) * 2003-01-15 2005-03-29 Nalco Company Method of using high molecular weight water soluble polymers in membrane bioreactor systems

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See references of WO2004028986A2 *

Also Published As

Publication number Publication date
NO20051991L (no) 2005-05-30
UA80724C2 (en) 2007-10-25
AU2003276364A1 (en) 2004-04-19
MXPA05003269A (es) 2005-07-05
JP2006500208A (ja) 2006-01-05
KR20050043986A (ko) 2005-05-11
US7135115B2 (en) 2006-11-14
BR0314842A (pt) 2005-08-09
US20060037909A1 (en) 2006-02-23
CN1684913A (zh) 2005-10-19
DE03798216T1 (de) 2005-09-29
ES2239935T1 (es) 2005-10-16
RU2321552C2 (ru) 2008-04-10
RU2005112241A (ru) 2005-09-10
HK1081517A1 (en) 2006-05-19
WO2004028986A2 (fr) 2004-04-08
WO2004028986A3 (fr) 2004-05-13
FR2844784B1 (fr) 2004-11-05
TR200502228T3 (tr) 2005-08-22
CA2500135A1 (fr) 2004-04-08
FR2844784A1 (fr) 2004-03-26
CN1293001C (zh) 2007-01-03
PL376562A1 (pl) 2006-01-09

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