FR2812627A1 - CONTINUOUS INDUSTRIAL WASTEWATER TREATMENT PROCESS AND DEVICES FOR ITS IMPLEMENTATION - Google Patents
CONTINUOUS INDUSTRIAL WASTEWATER TREATMENT PROCESS AND DEVICES FOR ITS IMPLEMENTATION Download PDFInfo
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- FR2812627A1 FR2812627A1 FR0010397A FR0010397A FR2812627A1 FR 2812627 A1 FR2812627 A1 FR 2812627A1 FR 0010397 A FR0010397 A FR 0010397A FR 0010397 A FR0010397 A FR 0010397A FR 2812627 A1 FR2812627 A1 FR 2812627A1
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- 238000000034 method Methods 0.000 title claims abstract description 27
- 239000010842 industrial wastewater Substances 0.000 title claims abstract description 10
- 238000004065 wastewater treatment Methods 0.000 title claims abstract 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 29
- 238000000746 purification Methods 0.000 claims abstract description 13
- 238000004519 manufacturing process Methods 0.000 claims abstract description 11
- 239000012528 membrane Substances 0.000 claims abstract description 11
- 238000001704 evaporation Methods 0.000 claims abstract description 9
- 230000008020 evaporation Effects 0.000 claims abstract description 9
- 238000001914 filtration Methods 0.000 claims abstract description 8
- 239000010802 sludge Substances 0.000 claims description 18
- 239000000126 substance Substances 0.000 claims description 13
- 239000007788 liquid Substances 0.000 claims description 10
- 239000000463 material Substances 0.000 claims description 8
- 239000012465 retentate Substances 0.000 claims description 7
- 238000003860 storage Methods 0.000 claims description 6
- 239000003344 environmental pollutant Substances 0.000 claims description 5
- 239000012535 impurity Substances 0.000 claims description 5
- 231100000719 pollutant Toxicity 0.000 claims description 5
- 241000894006 Bacteria Species 0.000 claims description 4
- 238000010438 heat treatment Methods 0.000 claims description 4
- 238000009434 installation Methods 0.000 claims description 4
- 238000006386 neutralization reaction Methods 0.000 claims description 4
- 238000010521 absorption reaction Methods 0.000 claims description 3
- 238000005273 aeration Methods 0.000 claims description 3
- 238000006065 biodegradation reaction Methods 0.000 claims description 3
- 238000005260 corrosion Methods 0.000 claims description 3
- 238000002347 injection Methods 0.000 claims description 3
- 239000007924 injection Substances 0.000 claims description 3
- 239000000243 solution Substances 0.000 claims description 3
- 239000002351 wastewater Substances 0.000 claims description 3
- 238000007664 blowing Methods 0.000 claims description 2
- 230000006835 compression Effects 0.000 claims description 2
- 238000007906 compression Methods 0.000 claims description 2
- 238000009792 diffusion process Methods 0.000 claims description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 claims description 2
- 239000011707 mineral Substances 0.000 claims description 2
- 235000015097 nutrients Nutrition 0.000 claims description 2
- 238000005457 optimization Methods 0.000 claims description 2
- 238000004064 recycling Methods 0.000 claims description 2
- 239000012855 volatile organic compound Substances 0.000 claims description 2
- 239000002699 waste material Substances 0.000 claims description 2
- 230000003472 neutralizing effect Effects 0.000 claims 2
- 238000011084 recovery Methods 0.000 claims 2
- 238000013019 agitation Methods 0.000 claims 1
- 239000011248 coating agent Substances 0.000 claims 1
- 238000000576 coating method Methods 0.000 claims 1
- 238000003756 stirring Methods 0.000 claims 1
- 238000009423 ventilation Methods 0.000 claims 1
- 238000001311 chemical methods and process Methods 0.000 abstract 1
- 230000009466 transformation Effects 0.000 abstract 1
- 150000001805 chlorine compounds Chemical class 0.000 description 2
- 230000001143 conditioned effect Effects 0.000 description 2
- 238000012423 maintenance Methods 0.000 description 2
- 239000002028 Biomass Substances 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 230000001580 bacterial effect Effects 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000003112 inhibitor Substances 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000006213 oxygenation reaction Methods 0.000 description 1
- 210000004197 pelvis Anatomy 0.000 description 1
- 239000012466 permeate Substances 0.000 description 1
Classifications
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/24—Treatment of water, waste water, or sewage by flotation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/02—Biological treatment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/13—Treatment of sludge; Devices therefor by de-watering, drying or thickening by heating
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/12—Activated sludge processes
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/20—Sludge processing
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
- Physical Water Treatments (AREA)
Abstract
Procédé d'épuration en continu d'eaux usées industrielles et dispositifs pour sa mise en oeuvre, basé sur la combinaison de différents procédés : un traitement biologique aérobie, un procédé physico-chimique, un procédé d'évaporation et une technique membranaire par filtration tangentielle, disposés selon cet ordre pour constituer une station d'épuration d'eaux uséees résiduaires de toutes sortes, permettant la transformation de ces effluents aqueux pollués en eau recyclable dans un process industriel. Adapté aux besoins spécifiques de nombreuses industries et adaptable à des installations de traitement d'effluents aqueux existantes afin d'optimiser leur rendement, ce procédé d'épuration en continu d'eaux usées industrielles permet de traiter un ou plusieurs effluents différents selon leur degré de biodégradabilité et est particulièrement adapté à des variations de volume et de charge polluante des effluents.Process for the continuous purification of industrial wastewater and devices for its implementation, based on the combination of different processes: an aerobic biological treatment, a physico-chemical process, an evaporation process and a membrane technique by tangential filtration , arranged in this order to constitute a wastewater treatment plant of all kinds, allowing the transformation of these polluted aqueous effluents into recyclable water in an industrial process. Adapted to the specific needs of many industries and adaptable to existing aqueous effluent treatment plants in order to optimize their performance, this process of continuous purification of industrial wastewater makes it possible to treat one or more different effluents according to their degree of biodegradability and is particularly suitable for variations in volume and polluting load of effluents.
Description
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La présente invention concerne un procédé d'épuration en continu d'eaux usées industrielles et dispositifs pour sa mise en oeuvre. <Desc / Clms Page number 1>
The present invention relates to a process for the continuous purification of industrial wastewater and devices for its implementation.
Le traitement des eaux usées industrielles reposent sur un et/ou deux grands procédés: un traitement physico-chimique et/ou un traitement biologique. The treatment of industrial wastewater is based on one and / or two main processes: a physico-chemical treatment and / or a biological treatment.
-Le traitement physico-chimique consiste en l'ajout d'additifs chimiques contribuant à faire coaguler puis décanter les impuretés contenues dans l'eau. Cela permet de sortir d'un côté, des boues fortement chargées difficilement revalorisables, nécessitant des coûts de traitement ultérieur élevés, de l'autre, de l'eau, Les taux d'épuration dans ce type de procédé sont limités. -The physico-chemical treatment consists in adding chemical additives helping to coagulate then decant the impurities contained in the water. This allows to get out on one side, highly charged sludge difficult to revalorize, requiring high subsequent treatment costs, on the other, water. The purification rates in this type of process are limited.
-Le traitement biologique consiste à développer dans un bassin une faune bactérienne endogène capable de décomposer les molécules polluantes. L'effluent est admis à débit régulier. La taille du bassin est conditionnée par le temps nécessaire aux bactéries pour digérer les molécules polluantes. Un décanteur permet ensuite de séparer les boues biologiques de l'eau traitée. -Biological treatment consists in developing an endogenous bacterial fauna capable of breaking down polluting molecules in a basin. The effluent is admitted at a regular rate. The size of the pelvis is conditioned by the time necessary for bacteria to digest polluting molecules. A decanter then separates the biological sludge from the treated water.
Le rapport de biodégradabilité de l'effluent est déterminant pour le choix du procédé de traitement. Lorsque les deux procédés sont associés, le traitement physico-chimique vient toujours en amont du traitement biologique. The biodegradability ratio of the effluent is decisive for the choice of the treatment process. When the two processes are combined, the physico-chemical treatment always comes before the biological treatment.
Dans certaines industries, les effluents sont très complexes et proviennent de plusieurs ateliers. Leur composition complexe limite souvent le rendement de la station d'épuration biologique du fait de la présence d'une DCO non-précipitable et d'inhibiteurs biologiques etc..., qui nuisent au fonctionnement et à l'efficacité de la biomasse. In some industries, the effluents are very complex and come from several workshops. Their complex composition often limits the performance of the biological treatment plant due to the presence of non-precipitable COD and biological inhibitors, etc., which adversely affect the functioning and efficiency of the biomass.
Pour remédier à ces inconvénients le procédé suivant 15nvention permet de traiter un ou plusieurs effluents différents selon leur degré de biodégradabilité et permet de transformer des eaux usées fortement polluées en eau claire recyclable en limitant la production de déchets tels que les boues. To remedy these drawbacks, the process according to the invention makes it possible to treat one or more different effluents according to their degree of biodegradability and makes it possible to transform highly polluted waste water into recyclable clear water by limiting the production of waste such as sludge.
Adapté aux besoins spécifiques de nombreuses industries ce procédé d'épuration en continu permet une capacité de traitement des effluents ( exprimée en DCO/jour ) particulièrement élevée. De plus, sa modularité permet de l'adapter à des installations de traitement d'effluents existantes afin d'augmenter leur rendement. Adapted to the specific needs of many industries, this continuous purification process allows a particularly high effluent treatment capacity (expressed in COD / day). In addition, its modularity allows it to be adapted to existing effluent treatment installations in order to increase their efficiency.
Il est caractérisé par les moyens mis en oeuvre, et plus particulièrement, par la combinaison de différents procédés : un traitement biologique aérobie, un procédé physico-chimique, un procédé d'évaporation et une technique membranaire par filtration tangentielle, disposés selon cet ordre pour constituer une station de traitement et de dépollution en continu d'effluents aqueux de toutes sortes. La figure unique représente à titre d'exemple non limitatif; un diagramme d'un mode de réalisation suivant l'invention où l'effluent A, après neutralisation du pH (3) par diffusion dans le liquide et absorption du neutralisant (4), arrive dans un réacteur biologique (1). C'est dans ce réservoir, en matériau adapté, dimensionné selon le temps nécessaire aux bactéries endogènes ou exogènes, sélectionnées et ensemencées avec des nutriments à des fréquences et des quantités déterminées pour digérer les molécules polluantes et selon les varations de volume et de charge polluante de l'effluent, que cet effluent A est porté à une température de 25-30 C. Il est agité (6) et aéré en permanence par l'air insufflé produit par un compresseur (7) et injecté par une rampe d'aération (5), à travers de fines buses. Cet air comprimé insufflé, est fonction du volume du réacteur et de l'effluent et permet une évaporation de cet effluent. It is characterized by the means used, and more particularly, by the combination of different processes: an aerobic biological treatment, a physicochemical process, an evaporation process and a membrane technique by tangential filtration, arranged in this order to constitute a continuous treatment and depollution station of aqueous effluents of all kinds. The single figure shows by way of nonlimiting example; a diagram of an embodiment according to the invention where the effluent A, after neutralization of the pH (3) by diffusion in the liquid and absorption of the neutralizer (4), arrives in a biological reactor (1). It is in this tank, in suitable material, sized according to the time necessary for endogenous or exogenous bacteria, selected and seeded with nutrients at frequencies and determined quantities to digest the polluting molecules and according to the variations in volume and polluting load. of the effluent, that this effluent A is brought to a temperature of 25-30 C. It is agitated (6) and permanently aerated by the blown air produced by a compressor (7) and injected by an aeration ramp (5), through fine nozzles. This blown compressed air is a function of the volume of the reactor and of the effluent and allows evaporation of this effluent.
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Cette oxygénation est nécessaire à l'entretien et au développement des bactéries endogènes ou exogènes spécifiques à l'effluent, permettant de digérer les matières biodégradables de cet effluent A. Chaque jour, un volume déterminé d'effluent du bioréacteur (1), transite par le traitement physico-chimique constitué de plusieurs compartiments, afin de permettre aux molécules de l'effluent A, dispersées dans les solutions ( 8, 9, 10 et 11 ) et partiellement biodégradées, d'être additionnées de produits chimiques qui les coagulent en gros flocs insolubles dans l'eau. Ces flocs sont remontés à la surface de l'eau en insufflant de l'eau pressurisée : les fines bulles d'air se fixant sur les flocs, les entraînent vers la surface de l'eau qui est écrémée mécaniquement. Ces boues écrémées liquides (13) sont envoyées (14) vers un bioréacteur (2), tandis que l'eau (12) est orientée vers une cuve de stockage ( 18) pour subir un traitement membranaire final par filtration tangentielle lorsque les paramètres chimiques de Peau l'imposent , notamment en matière de DCO résiduelle, de conductivité, de chlorures etc..., aux fins d'un recyclage de l'eau traitée dans le process industriel. This oxygenation is necessary for the maintenance and development of endogenous or exogenous bacteria specific to the effluent, making it possible to digest the biodegradable materials of this effluent A. Each day, a determined volume of effluent from the bioreactor (1) passes through the physico-chemical treatment consisting of several compartments, in order to allow the molecules of effluent A, dispersed in the solutions (8, 9, 10 and 11) and partially biodegraded, to be added with chemicals which coagulate them roughly water-insoluble flocs. These flocs are raised to the surface of the water by blowing pressurized water: the fine air bubbles attaching to the flocs, entrain them towards the surface of the water which is mechanically skimmed. These liquid skimmed sludges (13) are sent (14) to a bioreactor (2), while the water (12) is directed to a storage tank (18) to undergo a final membrane treatment by tangential filtration when the chemical parameters of water impose it, especially in terms of residual COD, conductivity, chlorides etc ..., for the purpose of recycling treated water in the industrial process.
Dans le réacteur (2.) les boues sont stockées. Ce bioréacteur (2) est prévu aussi pour recevoir un effluent B, pouvant être constitué de plusieurs effluents, dont le degré de biodégradabilité est plus lent que celui de l'effluent A. Le dïmensionnement de ce réacteur est conditionné par le volume de l'effluent B , par le temps nécessaire à sa biodégradation ainsi qu'au volume des boues liquides issues du traitement physico-chimique et au rétentat produit par le procédé membranaire par filtration tangentielle. In the reactor (2.) the sludge is stored. This bioreactor (2) is also designed to receive an effluent B, which may consist of several effluents, the degree of biodegradability of which is slower than that of effluent A. The dimensioning of this reactor is conditioned by the volume of the effluent B, by the time necessary for its biodegradation as well as the volume of the liquid sludge from the physico-chemical treatment and the retentate produced by the membrane process by tangential filtration.
Ce réacteur (2) en matériau adapté, dont la face interne est traitée d'une protection thermique et anti-corrosive, peut , par un système de chauffage, notamment par récupération des calories du process industriel, être porté à une température de 50 à 70 C. Cette température, conjuguée à l'injection permanente d'air comprimé, permet une évaporation importante de cet effluent sans pollution atmosphérique. En effet, l'effluent B, agité (6) et aéré (5), est mélangé aux boues liquides (l3) qui, progressivement, s'inactivent biologiquement mais demeurent chimiquement actives pour l'absorption des polluants de cet effluent B. Cette caractéristique permet de pièger les composés organiques volatiles et les vapeurs polluantes. Une injection d'air comprimé, à travers de fores buses, de l'ordre de 130 m3/heure, permet d'évaporer, à la température précitée, environ 10 m3 / jour (effluent. L'évaporation provoquée dans les bioréacteurs (1) et (2) permet une optimisation du procédé selon les variations de volume et de charge polluante du flux entrant. This reactor (2) of suitable material, the internal face of which is treated with thermal and anti-corrosion protection, can, by a heating system, in particular by recovering calories from the industrial process, be brought to a temperature of 50 to 70 C. This temperature, combined with the permanent injection of compressed air, allows significant evaporation of this effluent without atmospheric pollution. Indeed, effluent B, agitated (6) and aerated (5), is mixed with liquid sludge (13) which gradually become biologically inactive but remain chemically active for the absorption of pollutants from this effluent B. This characteristic allows trapping volatile organic compounds and polluting vapors. An injection of compressed air, through nozzle nozzles, of the order of 130 m3 / hour, makes it possible to evaporate, at the abovementioned temperature, about 10 m3 / day (effluent. The evaporation caused in the bioreactors (1 ) and (2) allows an optimization of the process according to the variations in volume and polluting load of the incoming flow.
Périodiquement, le contenu du réacteur (2) est orienté vers une cuve de neutralisation (15) et vers l'unité de compression et de déshydratation mécanique (16) afin de conditionner des gâteaux de boues compressées afin de les évacuer hors site pour être traitées et valorisées. L'eau résiduelle (17) du traitement des boues, est orientée vers le bioréacteur (1) pour y être mélangée à l'effluent A et y être traitée biologiquement. Une quantité importante de molécules polluantes de l'effluent B ayant été digérées pendant le séjour dans le bioréacteur (2) , après déshydratation des boues, cet effluent peut rejoindre le bioréacteur (1) pour compléter sa biodégradabilité. Periodically, the contents of the reactor (2) are directed to a neutralization tank (15) and to the compression and mechanical dewatering unit (16) in order to condition compressed sludge cakes in order to evacuate them off site for treatment. and valued. The residual water (17) from the sludge treatment is directed to the bioreactor (1) to be mixed there with the effluent A and to be treated therein biologically. A large quantity of pollutant molecules from effluent B having been digested during the stay in the bioreactor (2), after dewatering of the sludge, this effluent can join the bioreactor (1) to complete its biodegradability.
Après le traitement physico-chimique, l'eau (12) est orientée vers une cuve de stockage (18). Une pompe (alimentation (19) alimente un bac de concentration (20). Une pompe de recirculation (21) fait circuler l'eau (12), selon une pression déterminée. Cette eau (12) passe par un module- carter, en matériau adapté, servant de logement à des membranes (22), de type organiques ou After the physico-chemical treatment, the water (12) is directed to a storage tank (18). A pump (supply (19) feeds a concentration tank (20). A recirculation pump (21) circulates the water (12), according to a determined pressure. This water (12) passes through a housing module, suitable material serving as a housing for membranes (22), of organic type or
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ou minérales, déterminées en fonction de leur degré de porosité. Un perméat (23), débarassé de ses impuretés, est évacué en permanence vers une cuve de stockage (25). Une pompe d'alimentation (26) oriente cette eau traitée (23) vers le process industriel. Un rétentat ou concentrat d'impuretés (24), retourne vers le bac de concentration (20) et est évacué périodiquement vers le réacteur (2). L'intervention du procédé membranaire par filtration tangentielle en fin de procédé d'épuration permet d'une part, d'éliminer les problèmes de colmatage dus à de trop fortes charges polluantes, d'autre part, de développer un traitement particulièrement pointu afin d'obtenir une eau de qualité répondant parfaitement aux impératifs d'un process industriel et que n'autorisent pas le traitement biologique complété par le traitement physico-chimique. Avantageusement, ce traitement membranaire additionnel, permet d'éliminer une DCO non-précipitable, des matières en suspension, des micro-organismes, des chlorures etc-, afin de produire une eau recyclable, de qualité constante dans le temps, pouvant répondre aux critères les plus sélectifs d'un process industriel. Adapté aux besoins spécifiques de nombreuses industries et adaptable à des installations de traitement d'eflluents afin d'optimiser leur rendement, ce procédé d'épuration en continu apporte des solutions techniques sûres, économiques et pratiques, avec une occupation au sol réduite et une maintenance simplifiée, aux industriels qui doivent traiter leurs eaux usées, en préservant l'environnement. or mineral, determined according to their degree of porosity. A permeate (23), freed of its impurities, is permanently evacuated to a storage tank (25). A feed pump (26) directs this treated water (23) to the industrial process. A retentate or concentrate of impurities (24) returns to the concentration tank (20) and is periodically removed to the reactor (2). The intervention of the membrane process by tangential filtration at the end of the purification process makes it possible, on the one hand, to eliminate the problems of clogging due to too high polluting loads, on the other hand, to develop a particularly precise treatment in order to '' obtain quality water that perfectly meets the requirements of an industrial process and that is not authorized by biological treatment supplemented by physico-chemical treatment. Advantageously, this additional membrane treatment makes it possible to eliminate non-precipitable COD, suspended matter, microorganisms, chlorides, etc., in order to produce recyclable water, of constant quality over time, which can meet the criteria. the most selective of an industrial process. Adapted to the specific needs of many industries and adaptable to effluent treatment plants in order to optimize their performance, this continuous purification process provides safe, economical and practical technical solutions, with reduced floor space and maintenance simplified, to industrialists who must treat their wastewater while preserving the environment.
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Claims (1)
Priority Applications (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| FR0010397A FR2812627B1 (en) | 2000-08-07 | 2000-08-07 | CONTINUOUS INDUSTRIAL WASTEWATER TREATMENT PROCESS AND DEVICES FOR ITS IMPLEMENTATION |
| AU2001284104A AU2001284104A1 (en) | 2000-08-07 | 2001-08-02 | Installation and method for purifying waste water or effluents in particular industrial |
| PCT/FR2001/002533 WO2002012138A1 (en) | 2000-08-07 | 2001-08-02 | Installation and method for purifying waste water or effluents in particular industrial |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| FR0010397A FR2812627B1 (en) | 2000-08-07 | 2000-08-07 | CONTINUOUS INDUSTRIAL WASTEWATER TREATMENT PROCESS AND DEVICES FOR ITS IMPLEMENTATION |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| FR2812627A1 true FR2812627A1 (en) | 2002-02-08 |
| FR2812627B1 FR2812627B1 (en) | 2003-02-21 |
Family
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Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| FR0010397A Expired - Fee Related FR2812627B1 (en) | 2000-08-07 | 2000-08-07 | CONTINUOUS INDUSTRIAL WASTEWATER TREATMENT PROCESS AND DEVICES FOR ITS IMPLEMENTATION |
Country Status (3)
| Country | Link |
|---|---|
| AU (1) | AU2001284104A1 (en) |
| FR (1) | FR2812627B1 (en) |
| WO (1) | WO2002012138A1 (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN113244694A (en) * | 2021-05-17 | 2021-08-13 | 江苏蒲公英环境工程有限公司 | Sewage precipitation treatment system |
| CN115259617A (en) * | 2022-06-15 | 2022-11-01 | 湖北济新源生态科技有限责任公司 | Sludge drying system |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB0110282D0 (en) * | 2001-04-26 | 2001-06-20 | Hamworthy Kse Ltd | Liquid waste treatment system |
| US6692642B2 (en) * | 2002-04-30 | 2004-02-17 | International Waste Management Systems | Organic slurry treatment process |
| RU2343122C1 (en) * | 2007-03-09 | 2009-01-10 | Николай Иванович Куликов | Completely-block modular clearing station |
| RU2607818C1 (en) * | 2015-12-16 | 2017-01-20 | Геннадий Михайлович Зубов | System of waste waters zero waste disposal |
| CN112794519A (en) * | 2020-12-31 | 2021-05-14 | 苏州莱仕德机械科技有限公司 | High-end intelligent direct drinking water manufacturing multilayer purifying equipment |
Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS55155798A (en) * | 1979-05-23 | 1980-12-04 | Ebara Infilco Co Ltd | Treating method of organic waste water |
| DE3532390A1 (en) * | 1984-09-12 | 1986-06-19 | Carl Still Gmbh & Co Kg, 4350 Recklinghausen | Process for treating waste water arising in coking or other coal upgrading processes |
| JPS62152600A (en) * | 1985-12-25 | 1987-07-07 | Ebara Infilco Co Ltd | Treatment of oozing out waste contaminated water |
| FR2684094A1 (en) * | 1991-11-22 | 1993-05-28 | Regie Autonome Transports | Process for the treatment of aqueous effluents by bioassisted tangential ultrafiltration |
| WO1995021140A1 (en) * | 1994-02-04 | 1995-08-10 | G.C.M. Geodetics Construction Maintenance | Method for processing semi-liquid manure and the device to be used |
| EP0990622A2 (en) * | 1998-09-30 | 2000-04-05 | Bernd-Ulrich Wilk | Process and device for biological waste water purification |
-
2000
- 2000-08-07 FR FR0010397A patent/FR2812627B1/en not_active Expired - Fee Related
-
2001
- 2001-08-02 AU AU2001284104A patent/AU2001284104A1/en not_active Abandoned
- 2001-08-02 WO PCT/FR2001/002533 patent/WO2002012138A1/en not_active Ceased
Patent Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS55155798A (en) * | 1979-05-23 | 1980-12-04 | Ebara Infilco Co Ltd | Treating method of organic waste water |
| DE3532390A1 (en) * | 1984-09-12 | 1986-06-19 | Carl Still Gmbh & Co Kg, 4350 Recklinghausen | Process for treating waste water arising in coking or other coal upgrading processes |
| JPS62152600A (en) * | 1985-12-25 | 1987-07-07 | Ebara Infilco Co Ltd | Treatment of oozing out waste contaminated water |
| FR2684094A1 (en) * | 1991-11-22 | 1993-05-28 | Regie Autonome Transports | Process for the treatment of aqueous effluents by bioassisted tangential ultrafiltration |
| WO1995021140A1 (en) * | 1994-02-04 | 1995-08-10 | G.C.M. Geodetics Construction Maintenance | Method for processing semi-liquid manure and the device to be used |
| EP0990622A2 (en) * | 1998-09-30 | 2000-04-05 | Bernd-Ulrich Wilk | Process and device for biological waste water purification |
Non-Patent Citations (2)
| Title |
|---|
| PATENT ABSTRACTS OF JAPAN vol. 005, no. 031 (C - 045) 25 February 1981 (1981-02-25) * |
| PATENT ABSTRACTS OF JAPAN vol. 011, no. 381 (C - 464) 12 December 1987 (1987-12-12) * |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN113244694A (en) * | 2021-05-17 | 2021-08-13 | 江苏蒲公英环境工程有限公司 | Sewage precipitation treatment system |
| CN113244694B (en) * | 2021-05-17 | 2022-01-14 | 江苏蒲公英环境工程有限公司 | Sewage precipitation treatment system |
| CN115259617A (en) * | 2022-06-15 | 2022-11-01 | 湖北济新源生态科技有限责任公司 | Sludge drying system |
Also Published As
| Publication number | Publication date |
|---|---|
| WO2002012138A1 (en) | 2002-02-14 |
| FR2812627B1 (en) | 2003-02-21 |
| AU2001284104A1 (en) | 2002-02-18 |
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| ST | Notification of lapse |
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