WO2018188317A1 - Réacteur anaérobie et procédé de traitement anaérobie d'eaux usées - Google Patents

Réacteur anaérobie et procédé de traitement anaérobie d'eaux usées Download PDF

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Publication number
WO2018188317A1
WO2018188317A1 PCT/CN2017/107904 CN2017107904W WO2018188317A1 WO 2018188317 A1 WO2018188317 A1 WO 2018188317A1 CN 2017107904 W CN2017107904 W CN 2017107904W WO 2018188317 A1 WO2018188317 A1 WO 2018188317A1
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Prior art keywords
sludge
reaction chamber
anaerobic reactor
wastewater
scraping plate
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Ceased
Application number
PCT/CN2017/107904
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English (en)
Inventor
Jing Li
Sjoerd Hubertus Jozef Vellinga
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.)
Paques Environmental Technology (shanghai) Co Ltd
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Paques Environmental Technology (shanghai) Co Ltd
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
Priority claimed from CN201720387803.6U external-priority patent/CN206843182U/zh
Priority claimed from CN201710241490.8A external-priority patent/CN108726674A/zh
Application filed by Paques Environmental Technology (shanghai) Co Ltd filed Critical Paques Environmental Technology (shanghai) Co Ltd
Publication of WO2018188317A1 publication Critical patent/WO2018188317A1/fr
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

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    • 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
    • C02F3/28Anaerobic digestion processes
    • C02F3/2866Particular arrangements for anaerobic reactors

Definitions

  • the present disclosure relates to a field of environmental technologies, more particularly to an anaerobic reactor and an anaerobic wastewater treatment process used for wastewater treatment.
  • An anaerobic reactor is a common apparatus used for wastewater treatment, and the anaerobic reactor treats and converts oxygen consumption substances in the wastewater into biogas by means of anaerobic sludge in the anaerobic reactor.
  • the wastewater contains impurities, such as fiber (cow manure) , straw, or the like.
  • COD chemical oxygen demand
  • the wastewater does not undergo a fiber pretreatment before entering the anaerobic reactor.
  • Mixing homogeneity of the wastewater and the anaerobic sludge is an important factor influencing the treatment efficiency.
  • stirring is usually needed in the anaerobic reactor.
  • methods for improving mixing efficiency by stirring have their own problems, which need to be improved.
  • Stirring by compressed gas the compressed gas is introduced into the anaerobic reactor for stirring. This mode of stirring has problems of high energy consumption and high safety requirements for the anaerobic reactor.
  • Stirring by circulating pump wastewater in an upper portion of the anaerobic reactor is pumped to a lower portion of the anaerobic reactor by a circulating pump to produce an upward flow velocity, such that the wastewater and sludge can be flushed upwardly. This mode of stirring has stirring dead zones.
  • Mechanical stirring a stirring paddle is provided in the anaerobic reactor, the stirring paddle is driven to rotate by an electric motor arranged at a top of the anaerobic reactor through a driving shaft.
  • a distance between the stirring paddle and an inner bottom surface of the anaerobic reactor is usually one third of the height of the anaerobic reactor. If the stirring paddle is too close to the inner bottom surface, stirring energy will be lost and energy consumption and costs will increase. If the stirring paddle is too far away from the inner bottom surface, a stirring dead zone (i.e. a zone which cannot be stirred) often occurs on the bottom of the anaerobic reactor, affecting the mixing effect.
  • the present disclosure realizes the problems existing in the conventional stirring ways, and is intended to solve at least one of the technical problems in the related art at least to a certain extent.
  • the present disclosure proposes an anaerobic reactor and an anaerobic wastewater treatment process that does not need stirring and have low energy consumption. Furthermore, the mixing effect of the sludge and the wastewater is good, and the stirring dead zone on the bottom of the anaerobic reactor is reduced, thereby greatly improving the wastewater treatment efficiency.
  • the anaerobic reactor includes a tank body having a reaction chamber therein, the reaction chamber having a wastewater inlet and a biogas outlet, a sludge collecting groove being defined on a bottom surface of the reaction chamber, and a sludge outlet in communication with the sludge collecting groove being defined in an inner wall of the tank body; and a sludge scraper including a sludge scraping plate and a driving device, the sludge scraping plate being located on a bottom of the reaction chamber and configured to scrape sludge on the bottom surface of the reaction chamber into the sludge collecting groove, the driving device being arranged on a bottom of the tank body, connected to the sludge scraping plate, and configured to drive the sludge scraping plate to rotate.
  • the anaerobic wastewater treatment process includes supplying wastewater into a reaction chamber of an anaerobic reactor, and performing anaerobic wastewater treatment by utilizing sludge in the reaction chamber; scraping the sludge on a bottom surface of the reaction chamber into a sludge collecting groove on the bottom surface by means of a sludge scraper, and the sludge scraper including a sludge scraping plate and a driving device arranged on a bottom of the anaerobic reactor and configured to drive the sludge scraping plate; and discharging the sludge in the sludge collecting groove from the reaction chamber.
  • the sludge on the bottom of the reaction chamber is scraped into the sludge collecting groove by the sludge scraper, such that the sludge can be avoided from depositing on the bottom of the reaction chamber, and the mixing effect of the sludge and the wastewater can be improved. Furthermore, no stirring device is needed, so as to overcome problems brought by the conventional stirring ways. Since the driving device for driving the sludge scraper is arranged on the bottom of the tank body, the driving device can be connected to the sludge scraper without the long transmission shaft, such that the sludge scraper operates steadily and has little vibration and noise.
  • Fig. 1 illustrates a schematic view of an anaerobic reactor according to a first embodiment of the present disclosure.
  • Fig. 2 illustrates a schematic view of an anaerobic reactor according to a second embodiment of the present disclosure.
  • Fig. 3 illustrates a schematic view of an anaerobic reactor according to a third embodiment of the present disclosure.
  • Fig. 4 illustrates a top view of an anaerobic reactor according to an embodiment of the present disclosure.
  • Fig. 5 illustrates a schematic view of an anaerobic reactor according to a fourth embodiment of the present disclosure.
  • an anaerobic reactor includes a tank body 1 and a sludge scraper 4.
  • An inner cavity of the tank body 1 forms a reaction chamber 11.
  • the reaction chamber 11 defines a wastewater inlet 2 and a biogas outlet 3, wastewater is transmitted into the reaction chamber 11 through the wastewater inlet 2, and biogas produced in the reaction chamber 11 is discharged through the biogas outlet 3.
  • a sludge collecting groove 6 is defined on a bottom surface of the reaction chamber 11, and the sludge collecting groove 6 is configured to collect sludge on the bottom surface of the reaction chamber 11.
  • the term “collect” means that the sludge scraper 4 scrapes the sludge on the bottom surface of the reaction chamber 11 and concentrates the sludge into the sludge collecting groove 6.
  • the sludge scraper 4 includes a sludge scraping plate 41 and a driving device 5.
  • the sludge scraping plate 41 is located on a bottom of the reaction chamber 11, spaced apart from the bottom surface and a circumferential wall of the reaction chamber 11 at a preset distance, and configured to scrape the sludge on the bottom surface of the reaction chamber 11 into the sludge collecting groove 6.
  • the driving device 5 is arranged to a bottom of the tank body 1, connected to the sludge scraping plate 41, and configured to drive the sludge scraping plate 41 to rotate.
  • the sludge on the bottom of the reaction chamber 11 is scraped into the sludge collecting groove 6 to prevent the sludge in the reaction chamber 11 from depositing on the bottom of the reaction chamber 11.
  • At least a part of the sludge collected in the sludge collecting groove 6 can be returned to an upper portion of the reaction chamber 11.
  • all of the sludge in the sludge collecting groove 6 can be circulated and returned to the upper portion of the reaction chamber 11, or a part of the sludge can be returned to the upper portion of the reaction chamber 11 and the other part of the sludge can be discharged.
  • the driving device 5 for driving the sludge scraping plate 41 is also arranged to a lower portion of the tank body 1 instead of a top of the tank body 1, accordingly, the driving device 5 is not necessary to be connected to the sludge scraping plate 41 through a long transmission shaft and has little vibration, such that the sludge scraper operates steadily.
  • the sludge collected in the sludge collecting groove 6 can be returned into the reaction chamber 11 to be mixed with the wastewater.
  • the sludge on the bottom of the reaction chamber is not necessary to be stirred by a conventional stirring device, thereby solving problems brought by conventional stirring ways.
  • the tank body 1 defines the reaction chamber 11 therein, and the reaction chamber 11 has the wastewater inlet 2 and the biogas outlet 3.
  • the sludge collecting groove 6 is defined on the bottom surface of the reaction chamber 11 and configured to collect the sludge on the bottom surface of the reaction chamber 11.
  • the sludge scraper 4 includes the sludge scraping plate 41 and the driving device 5, and the sludge scraping plate 41 is configured to scrape the sludge on the bottom surface of the reaction chamber 11 into the sludge collecting groove 6.
  • the sludge scraping plate 41 is arranged adjacent to the bottom surface of the reaction chamber 11.
  • a distance between a lower edge of the sludge scraping plate 41 and the bottom surface of the reaction chamber 11 is smaller than 100 mm.
  • the driving device 5 is arranged to the bottom of the tank body 1, connected to the sludge scraping plate 41, and configured to drive the sludge scraping plate 41 to rotate.
  • a rotating speed of the sludge scraping plate 41 is smaller than 5 revolutions per hour, but it is not limited to this. In embodiments of the present disclosure, as long as the rotating speed of the sludge scraping plate 41 satisfies that the sludge scraping plate 41 can scrape the sludge on the bottom surface of the reaction chamber 11 without a substantial stirring function. It should be understood by those skilled in the art that, if the stirring is needed, the rotating speed of a stirring component configured to stir, such as a stirring paddle, is typically greater than a preset value. However, in embodiments of the present disclosure the sludge scraping plate 41 is configured to scrape the sludge on the bottom surface of the reaction chamber instead of stirring. Accordingly, the anaerobic reactor according to embodiments of the present disclosure does not have problems existing in conventional anaerobic reactors that require stirring.
  • the driving device 5 is a hydraulic motor, such that the driving device 5 can be immersed in the wastewater without being sealed, thereby simplifying the structure.
  • the driving device 5 can be driven by a power device located outside the tank body 1.
  • the anaerobic reactor further includes a circulating pump 7 having an inlet in communication with the sludge outlet (the sludge outlet is in communication with the sludge collecting groove 6 and defined in an inner wall of the tank body) of the sludge collecting groove 6 and an outlet in communication with the upper portion of the reaction chamber 11, and the circulating pump 7 is configured to pump at least a part of the sludge in the sludge collecting groove 6 to the upper portion of the reaction chamber 11, thereby improving a mixing effect of the sludge and the wastewater and improving a treatment effect of the wastewater.
  • the circulating pump 7 can be arranged outside the tank body 1.
  • the inlet of the circulating pump 7 is in communication with the sludge outlet of the sludge collecting groove 6, and the outlet of the circulating pump 7 is in communication with the upper portion of the reaction chamber 11.
  • At least a part of the sludge collected in the sludge collecting groove 6 enters the circulating pump 7 through the inlet of the circulating pump 7, under the pumping of the circulating pump 7, the sludge enters the reaction chamber 11 through the outlet of the circulating pump 7 to be mixed with the wastewater, such that the wastewater and the sludge can be mixed uniformly, and the treatment effect can be improved.
  • the circulating pump 7 pumps the sludge to the upper portion of the reaction chamber 11 in a tangent direction of the reaction chamber 11. That is to say, an opening (either a pipe hole or a nozzle) of the reaction chamber 11 connected to the circulating pump 7 is orientated in the tangent direction of the reaction chamber 11, the sludge is sprayed into the reaction chamber 11 in the tangent direction to make the wastewater in the reaction chamber 11 rotate in along the circumferential direction, thereby avoiding accumulation of floating stuff on the surface of wastewater. Furthermore, the wastewater and the sludge are mixed uniformly, such that the wastewater treatment efficiency is better. In some examples, the sludge is supplied to a position, below a liquid surface, in the upper portion of the reaction chamber 11 by the circulating pump 7, such that the mixing of the sludge and the wastewater can be achieved better.
  • the tank body 1 includes a cement bottom wall and an upper metal tank body arranged on the cement bottom wall and having an open lower end. An outer periphery of the cement bottom wall extends outwardly beyond an outer periphery of the upper metal tank body.
  • the cement bottom wall is provided with a sludge outlet pipe 12 therein, one end of the sludge outlet pipe 12 is connected to the sludge outlet of the sludge collecting groove 6 and the other end of the sludge outlet pipe is connected to the inlet of the circulating pump 7.
  • a ratio of length to diameter of the sludge outlet pipe 12 is smaller than 40: 1.
  • the sludge may contain fiber, or the like therein.
  • the sludge outlet pipe 12 can be blocked very easily when the sludge outlet pipe 12 exceeds a certain length.
  • the sludge outlet pipe 12 is very hard to clean in case of blocking, which not only affects the wastewater treatment, but also increases the maintenance cost.
  • the ratio of length to diameter of the sludge outlet pipe 12 is limited to be smaller than a preset value, such that the problem of blocking can be solved better.
  • the distance between the lower edge of the sludge scraping plate 41 and the bottom surface of the reaction chamber 11 is smaller than 100 mm.
  • the lower edge of the sludge scraping plate 41 is as close as possible to the bottom wall of the reaction chamber 11. In some optional examples, the distance is smaller than 100 mm.
  • the rotating speed of the sludge scraping plate 41 is smaller than 5 revolutions per hour. Thus, the sludge can be scraped and the energy consumption is reduced.
  • the sludge scraper 4 further includes a truss 42.
  • the sludge scraping plate 41 is connected to the truss 42, the truss 42 may be provided with a roller configured to roll on the bottom surface of the reaction chamber 11 so as to auxiliarily support the truss 42 and the sludge scraping plate 41.
  • the lower edge of the sludge scraping plate 41 may be provided with an elastic rubber sheet 411 in elastic contact with the bottom surface of the reaction chamber 11.
  • the elastic rubber sheet 411 is in contact with the bottom wall of the reaction chamber 11, thereby improving the sludge scraping effect and achieving a buffering function to prevent damages to the bottom surface of the reaction chamber 11 and the sludge scraper 4.
  • an outer edge of the sludge scraping plate 41 extends outwardly beyond an outer edge of the sludge collecting groove 6.
  • An inner side wall surface of the sludge collecting groove 6 is a bevel inclined outwardly and downwardly. Thus, the sludge on the bottom wall of the reaction chamber 11 can flow into the sludge collecting groove 6 more easily.
  • the driving device 5 includes the hydraulic motor
  • the sludge scraper 4 further includes a central shaft sleeve 43.
  • the sludge scraping plate 41 is mounted to the central shaft sleeve 43 and rotates with the rotation of the central shaft sleeve 43.
  • the hydraulic motor 5 is arranged in the central shaft sleeve 43, and an output shaft of the hydraulic motor 5 is connected to the central shaft sleeve 43 to drive the central shaft sleeve 43 to rotate.
  • the anaerobic reactor further includes a gas supply pipe 8, the gas supply pipe 8 is configured to transmit gas into the central shaft sleeve 43 to maintain a preset pressure in the central shaft sleeve 43, such that the wastewater in the reaction chamber 11 can be prevented from entering the central shaft sleeve 43, greatly prolonging the service life of the driving device 5.
  • the driving device 5 may employ an electric motor.
  • the driving device 5 includes the hydraulic motor or the electric motor
  • the sludge scraper 4 further includes the central shaft sleeve 43.
  • the sludge scraping plate 41 is mounted to the central shaft sleeve 43
  • the central shaft sleeve 43 is further provided with a sealing sleeve 44 therein, and a top end and an outer circumferential wall of the sealing sleeve 44 are spaced apart from the central shaft sleeve 43.
  • a lower end of the sealing sleeve 44 is arranged to the bottom wall of the reaction chamber 11, and the hydraulic motor or the electric motor is arranged in the sealing sleeve 44.
  • the output shaft of the hydraulic motor or the electric motor passes through an upper end of the sealing sleeve 44 and is connected to the central shaft sleeve 43.
  • the sealing sleeve 44 has a gas supply opening configured to supply the gas into the sealing sleeve 44 to maintain the preset pressure in the sealing sleeve 44 so as to prevent the wastewater in the reaction chamber 11 from entering the sealing sleeve 44.
  • the lower end of the sealing sleeve 44 is arranged in the bottom wall of the reaction chamber 11, and the gas supply opening is connected to a gas supply channel or the gas supply pipe 8 arranged in the bottom wall of the reaction chamber 11 and connected to an external gas source.
  • the sludge collecting groove 6 may be a single annular groove extending in a circumferential direction of the tank body 1 or a plurality of grooves spaced apart in the circumferential direction of the tank body 1.
  • one or more circulating pumps 7 may be provided.
  • the bottom surface of the reaction chamber 11 may be divided into a plurality of sludge scraping zones, a plurality of sludge scrapers is provided and corresponding to the plurality of sludge scraping zones, and each sludge scraping zone defines at least one sludge collecting groove 6 therein.
  • the upper portion of the reaction chamber 11 is provided with a circulating spray head 9, and the outlet of the circulating pump 7 is connected to the circulating spray head 9.
  • a wastewater spray head configured to spray the wastewater into the reaction chamber 11 is provided at the wastewater inlet 2.
  • the wastewater spray head supplies the wastewater to a position above the liquid surface in the reaction chamber in a tangent direction.
  • the wastewater spray head sprays the wastewater into the reaction chamber 11 in the tangent direction of the reaction chamber 11, the wastewater sprayed into the reaction chamber 11 causes the circumferential rotation motion of the wastewater in the reaction chamber 11, thereby avoiding the accumulation of the surface flotage of the wastewater.
  • the wastewater and the sludge are mixed uniformly, such that the wastewater treatment effect is better.
  • wastewater is supplied into a reaction chamber of an anaerobic reactor, such that an anaerobic wastewater treatment can be performed by utilizing sludge in the reaction chamber.
  • a sludge scraper scraps the sludge on a bottom surface of the reaction chamber into a sludge collecting groove on the bottom surface
  • the sludge scraper includes a sludge scraping plate and a driving device arranged on the bottom of the anaerobic reactor and configured to drive the sludge scraping plate.
  • the sludge in the sludge collecting groove id discharged from the reaction chamber.
  • At least a part of the sludge discharged from the sludge collecting groove is pumped to an upper portion of the reaction chamber in a tangent direction of the reaction chamber.
  • the at least a part of the sludge is pumped to a position above a liquid surface in the reaction chamber, and the wastewater is supplied into the reaction chamber in the tangent direction of the reaction chamber.
  • the sludge on the bottom of the reaction chamber is scraped into the sludge collecting groove by the sludge scraper, a part of the sludge can be circulated to the upper portion of the reaction chamber, such that the mixing effect of the sludge and the wastewater can be improved. Furthermore, no stirring device is needed, so as to overcome problems brought by the conventional stirring ways. Since the driving device for driving the sludge scraper is arranged on the bottom of the tank body, driving device can be connected to the sludge scraper without a long transmission shaft, such that the sludge scraper operates steadily and has little vibration and noise.
  • the anaerobic wastewater treatment process of the present disclosure does not need stirring and has low energy consumption. Furthermore, the mixing effect of the sludge and the wastewater is good, and stirring dead zone (i.e. a zone which cannot be stirred) on the bottom of the anaerobic reactor is reduced, thereby greatly improving the wastewater treatment effect.
  • first and second are used herein for purposes of description and are not intended to indicate or imply relative importance or significance.
  • the feature defined with “first” and “second” may comprise one or more of this feature.
  • the term “aplurality of” means two or more than two, unless specified otherwise.
  • the terms “mounted, ” “connected, ” “coupled, ” “fixed” and the like are used broadly, and may be, for example, fixed connections, detachable connections, or integral connections; may also be mechanical or electrical connections; may also be direct connections or indirect connections via intervening structures; may also be inner communications of two elements, unless limited otherwise.
  • the above terms can be understood by those skilled in the art according to specific situations.
  • a structure in which a first feature is “on” or “below” a second feature may include an embodiment in which the first feature is in direct contact with the second feature, and may also include an embodiment in which the first feature and the second feature are not in direct contact with each other, but are contacted via an additional feature formed therebetween.
  • a first feature “on, ” “above, ” or “on top of” a second feature may include an embodiment in which the first feature is right or obliquely “on, ” “above, ” or “on top of” the second feature, or just means that the first feature is at a height higher than that of the second feature.
  • first feature “below, ” “under, ” or “on bottom of” a second feature may include an embodiment in which the first feature is right or obliquely “below, ” “under, ” or “on bottom of” the second feature, or just means that the first feature is at a height lower than that of the second feature.

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  • Life Sciences & Earth Sciences (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Mixers Of The Rotary Stirring Type (AREA)

Abstract

L'invention concerne un réacteur anaérobie et un procédé de traitement anaérobie d'eaux usées. Le réacteur anaérobie comprend un corps de réservoir (1) et un racleur de boues (4). Le corps de réservoir (1) contient une chambre de réaction (11). La chambre de réaction (11) comporte une entrée d'eaux usées (2) et une sortie de biogaz (3). Une rainure de collecte de boues (6) est délimitée sur la surface inférieure de la chambre de réaction (11). Un tuyau de sortie de boues (12) en communication avec la rainure de collecte de boues (6) est délimité dans une paroi interne du corps de réservoir (1). Le racleur de boues (4) comprend une plaque de raclage de boues (41) et un dispositif d'entraînement (5). La plaque de raclage de boues (41) est située sur le fond de la chambre de réaction (11), et est conçue pour racler les boues sur la surface inférieure de la chambre de réaction (11) dans la rainure de collecte de boues (6). Le dispositif d'entraînement (5) est disposé sur le fond du corps de réservoir (1) et relié à la plaque de raclage de boues (41) pour l'entraîner en rotation.
PCT/CN2017/107904 2017-04-13 2017-10-26 Réacteur anaérobie et procédé de traitement anaérobie d'eaux usées Ceased WO2018188317A1 (fr)

Applications Claiming Priority (4)

Application Number Priority Date Filing Date Title
CN201710241490.8 2017-04-13
CN201720387803.6U CN206843182U (zh) 2017-04-13 2017-04-13 厌氧反应器
CN201720387803.6 2017-04-13
CN201710241490.8A CN108726674A (zh) 2017-04-13 2017-04-13 厌氧反应器和废水厌氧处理工艺

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Cited By (10)

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CN111099720A (zh) * 2018-10-26 2020-05-05 中国石油化工股份有限公司 一种污水生物处理反应器及其处理方法
CN111470700A (zh) * 2020-03-11 2020-07-31 西纯环保科技(上海)有限公司 一种厌氧外循环反应器
CN112194246A (zh) * 2020-09-11 2021-01-08 安徽国正环境工程技术有限公司 一种厌氧反应器及其搅拌装置
CN112645533A (zh) * 2019-10-12 2021-04-13 帕克环保技术(上海)有限公司 净化系统
CN113896321A (zh) * 2021-09-29 2022-01-07 兴源环境科技股份有限公司 一种厌氧废水处理装置
CN115108631A (zh) * 2021-03-17 2022-09-27 帕克环保技术(上海)有限公司 好氧反应器
CN115611420A (zh) * 2022-09-26 2023-01-17 中国恩菲工程技术有限公司 厌氧罐反应系统
CN116803922A (zh) * 2023-08-05 2023-09-26 福建省河山环保科技有限公司 一种污水处理厌氧反应器
CN118724298A (zh) * 2024-08-28 2024-10-01 内蒙古工业大学 一种废水处理膜生物反应器
CN118754309A (zh) * 2024-09-02 2024-10-11 陕西锦科环保工程有限公司 一种均匀布水的厌氧反应器

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Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111099720B (zh) * 2018-10-26 2022-05-03 中国石油化工股份有限公司 一种污水生物处理反应器及其处理方法
CN111099720A (zh) * 2018-10-26 2020-05-05 中国石油化工股份有限公司 一种污水生物处理反应器及其处理方法
CN112645533A (zh) * 2019-10-12 2021-04-13 帕克环保技术(上海)有限公司 净化系统
CN111470700A (zh) * 2020-03-11 2020-07-31 西纯环保科技(上海)有限公司 一种厌氧外循环反应器
CN112194246A (zh) * 2020-09-11 2021-01-08 安徽国正环境工程技术有限公司 一种厌氧反应器及其搅拌装置
CN115108631A (zh) * 2021-03-17 2022-09-27 帕克环保技术(上海)有限公司 好氧反应器
CN115108631B (zh) * 2021-03-17 2023-12-05 帕克环保技术(上海)有限公司 好氧反应器
CN113896321A (zh) * 2021-09-29 2022-01-07 兴源环境科技股份有限公司 一种厌氧废水处理装置
CN113896321B (zh) * 2021-09-29 2023-11-28 兴源环境科技股份有限公司 一种厌氧废水处理装置
CN115611420A (zh) * 2022-09-26 2023-01-17 中国恩菲工程技术有限公司 厌氧罐反应系统
CN116803922A (zh) * 2023-08-05 2023-09-26 福建省河山环保科技有限公司 一种污水处理厌氧反应器
CN118724298A (zh) * 2024-08-28 2024-10-01 内蒙古工业大学 一种废水处理膜生物反应器
CN118754309A (zh) * 2024-09-02 2024-10-11 陕西锦科环保工程有限公司 一种均匀布水的厌氧反应器

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