WO2013147671A1 - Treatment plant for sewage treatment - Google Patents

Treatment plant for sewage treatment Download PDF

Info

Publication number
WO2013147671A1
WO2013147671A1 PCT/SE2013/050123 SE2013050123W WO2013147671A1 WO 2013147671 A1 WO2013147671 A1 WO 2013147671A1 SE 2013050123 W SE2013050123 W SE 2013050123W WO 2013147671 A1 WO2013147671 A1 WO 2013147671A1
Authority
WO
WIPO (PCT)
Prior art keywords
partition wall
circulation tank
treatment plant
waste water
plant according
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.)
Ceased
Application number
PCT/SE2013/050123
Other languages
French (fr)
Inventor
Lars UBY
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.)
Xylem Water Solutions AB
Original Assignee
Xylem Water Solutions AB
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 to RU2014143248A priority Critical patent/RU2014143248A/en
Priority to EP13769485.7A priority patent/EP2831002A4/en
Priority to MX2014010742A priority patent/MX2014010742A/en
Priority to CA2868822A priority patent/CA2868822A1/en
Priority to CN201380017267.5A priority patent/CN104245600B/en
Priority to KR1020147030084A priority patent/KR20140138334A/en
Application filed by Xylem Water Solutions AB filed Critical Xylem Water Solutions AB
Priority to US14/389,070 priority patent/US20150076717A1/en
Priority to AU2013240630A priority patent/AU2013240630B2/en
Priority to HK15102267.5A priority patent/HK1201810A1/en
Publication of WO2013147671A1 publication Critical patent/WO2013147671A1/en
Anticipated expiration legal-status Critical
Priority to IN2361KON2014 priority patent/IN2014KN02361A/en
Ceased legal-status Critical Current

Links

Classifications

    • 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
    • C02F3/22Activated sludge processes using circulation pipes
    • 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
    • C02F3/1257Oxidation ditches
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01FMIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
    • B01F23/00Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
    • B01F23/20Mixing gases with liquids
    • B01F23/23Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
    • B01F23/231Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids by bubbling
    • B01F23/23105Arrangement or manipulation of the gas bubbling devices
    • B01F23/2311Mounting the bubbling devices or the diffusers
    • B01F23/23112Mounting the bubbling devices or the diffusers comprising the use of flow guiding elements adjacent or above the gas stream
    • B01F23/231121Mounting the bubbling devices or the diffusers comprising the use of flow guiding elements adjacent or above the gas stream the flow guiding elements being baffles, tubes or walls
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2203/00Apparatus and plants for the biological treatment of water, waste water or sewage
    • C02F2203/006Apparatus and plants for the biological treatment of water, waste water or sewage details of construction, e.g. specially adapted seals, modules, connections
    • 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
    • C02F3/20Activated sludge processes using diffusers
    • C02F3/201Perforated, resilient plastic diffusers, e.g. membranes, sheets, foils, tubes, hoses
    • 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 generally to a treatment plant for waste water treatment.
  • the present invention relates to a treatment plant for biological waste water treatment, the treatment plant comprising a circulation tank, which is arranged to accommodate waste water up to a predetermined filling height, and at least one aerator section arranged at the bottom of the circulation tank.
  • the circulation tank has a predetermined direction of flow along which the waste water is arranged to flow, and the aerator section is arranged to supply gas bubbles to the waste water when the same passes the aerator section.
  • a circulation tank, or oxidation ditch is an open, endless tank that is used in biological purification, or oxidation, of waste water, in which the waste water is brought to flow along the circulation tank and thereby brought to pass different zones in the circulation tank.
  • biological purification usually the waste water is cleaned from nitrogen and biological material by microorganisms decomposing the biological material into carbon dioxide and water, and bacteria converting the waterborne nitrogen into aerial nitrogen.
  • the waterborne nitrogen is not eliminated, this entails the risk of over- fertilization of watercourses and the biological material is strongly oxygen depleting, which gives watercourses
  • aerator section is arranged in the aerated zone.
  • oxygen is added to the waste water by gas bubbles being discharged into the waste water by means of aerator sections arranged at the bottom of the circulation tank.
  • Microorganisms in the so-called activated sludge use the supplied oxygen to decompose the biological material found in the waste water.
  • the waste water should circulate along the circulation tank, and a known attempt to provide a main liquid flow along the circulation tank and to simultaneously obtain uniform aeration of the waste water is disclosed in the withdrawn US patent application 09/801,667.
  • This patent application shows a plant that utilizes the lift of the air in order to create a main liquid flow.
  • the waste water is entered into the aerator section in the vicinity of the bottom of the circulation tank and is discharged on the opposite side of the aerator section in the vicinity of the liquid surface; in this way, the liquid flow and the air flow have more or less the same direction above the aerator section.
  • the main liquid flow is provided by the fact that a first transverse partition wall, arranged upstream the aerator section, extends down into the waste water from above the liquid surface and that a second transverse partition wall, arranged downstream the aerator section, extends up from the bottom of the circulation tank. It is important that the lower end of the first, upper partition wall is on a level that is situated below half the height of the circulation tank, and that the upper end of the second, lower partition wall is on a level that is situated above half the height of the circulation tank. In this way, a liquid flow past the aerator section is created, at the same time as the rise velocity of the air in the waste water is increased.
  • a large disadvantage of the disclosed plant is thus that the supplied air will rise quickly to the surface and leave the waste water.
  • a further disadvantage is that only the upper liquid volume downstream the aerator section will be provided with a flow rate along the circulation tank at the same time as the lower liquid volume will stand still, or recirculate slowly, downstream the aerator section, whereupon the biological material in the waste water risks being accumulated at the bottom of the circulation tank.
  • a primary object of the invention is to provide an improved treatment plant of the initially defined type, which provides a more uniform main liquid flow along the circulation tank when considering a cross-section of the circulation tank downstream the aerator section.
  • a treatment plant of the type initially defined is provided, which is charac- terized in that the same comprises a partition wall arranged transversely to the circulation tank downstream the aerator section, which partition wall has an upper end that in the vertical direction is situated at a height that is lower than 25 % of the predetermined filling height of the circulation tank.
  • the present invention is based on the understanding that a low partition wall arranged downstream the aerator section stops the rearwardly directed return liquid flow found closest to the bottom of the circulation tank in the area downstream the aerator section, with the purpose of lowering the rise velocity of the air and with the purpose of recovering the linear momentum of the rearwardly directed return flow by means of the reaction force of the partition wall on the waste water, which strengthens the main liquid flow, at the same time as the main liquid flow that passes the aerator section along the circulation tank is affected to an as small as possible extent .
  • the upper end of the partition wall in the vertical direction is situated at a height that is less than 20 % of the filling height, preferably less than 15 %.
  • the partition wall has a lower end that in the vertical direction is situated at a distance from the bottom of the circulation tank.
  • the distance between the lower end of the partition wall and the bottom of the circulation tank is more than 5 cm and less than 15 cm. This entails that solid material found in the waste water does not risk being accumulated at the partition wall but can pass freely under the same.
  • the partition wall has a first surface turned downstream, which first surface is plane.
  • the first surface of the partition wall is essentially vertical. A plane and vertical surface of the partition wall turned downstream gives maximum effective target area in relation to the rearwardly directed return liquid flow with a minimal size of the partition wall.
  • the partition wall has a second surface turned upstream, which second surface is curved in the upstream direction, with the purpose of minimizing the effect on the main liquid flow that passes the aerator section along the circulation tank.
  • the treatment plant comprises at least one flow generating machine arranged upstream said at least one aerator section, which flow generating machine is arranged to generate the main liquid flow along said circulation tank.
  • Fig. 1 is a schematic elevated view from above of a treat- ment plant according to the invention
  • Fig. 2 is a schematic side view of the aerator section and partition wall of the treatment plant
  • Fig. 3 is a schematic cross-sectional view of the partition wall of the treatment plant according to a first embodiment
  • Fig. 4 is a schematic cross-sectional view of the partition wall of the treatment plant according to a second embodiment
  • Fig. 5 is a schematic cross-sectional view of the partition wall of the treatment plant according to a third embodiment .
  • the present invention relates to a treatment plant, generally designated 1, for waste water treatment comprising
  • the treatment plant comprises an endless circulation tank 2, or oxidation ditch, which in the embodiment shown consists of an elongate tank having rounded ends and comprising a centrally placed longitudinal partition 3, whereupon the circulation tank 2 obtains two
  • circulation tanks may have other feasible shapes, for instance an annular shape or a serpentine shape; accordingly, the circulation tank may comprise more straight and redirecting channel segments, respectively, or have an entirely circular/elliptical path shape.
  • the circulation tank 2 is arranged to accommodate waste water up to a predetermined filling height H, even if the actual liquid level in operation may be below as well as exceed said filling height H without the present invention being affected.
  • the waste water is cleaned batch-wise, or continuously, in a treatment plant 1 according to the invention, and with a waste water volume that reaches up to said filling height H, an optimal utilization of the treatment plant 1 is obtained.
  • a typical filling height H is in the order of 3-4 m, but can be as high as 7-8.
  • the circulation tank 2 is arranged with a predetermined direction of flow, schematically illustrated by means of the arrow 4, along which the waste water is intended to flow, while forming a main liquid flow. According to the invention it is of secondary importance how the main liquid flow is
  • the treatment plant 1 comprises at least one aerator section 5 that is arranged in an aerated zone of the circulation tank 2.
  • the aerator section 5 Upstream the aerator section 5, there is found a non-aerated zone of the circulation tank 2.
  • the aerator section 5 is arranged in the beginning of a straight channel segment, even if other positions are feasible.
  • Said at least one aerator section 5 is arranged at the bottom of the circulation tank 2 and is arranged to supply oxygen- containing gas bubbles, such as air or pure oxygen, to the waste water, with the purpose of supplying oxygen to the waste water.
  • the aerator section 5 consists, for instance, of a vast number of diffusers or aerator elements, which jointly cover the entire or the main part of the width of the circulation tank 2, a typical width of the circulation tank 2 is in the order of 10-15 m.
  • the length of the aerator section 5 along the circulation tank 2 is in the order of 5- 25 % of the entire length of the circulation tank 2.
  • the treatment plant 1 comprises two or more aerator sections 5, which preferably are equidistantly arranged along the circulation tank 2.
  • the treatment plant 1 comprises at least one flow generating machine 6 arranged upstream said at least one aerator section 5.
  • the flow generating machine 6 is arranged to generate a flow of waste water along said circulation tank 2, and may consist of one or more so-called slow-moving agitators.
  • the treatment plant 1 comprises flow generating machines 6 in two or more positions, which preferably are equidistantly arranged along the circulation tank 2.
  • the partition wall 7 comprises also at least one partition wall 7 arranged transversely to the circulation tank 2 downstream said at least one aerator section 5.
  • the partition wall 7 extends transversely to the direction of flow 4 of the circulation tank 2.
  • the partition wall 7 is arranged perpendicular to the direction of flow 4 of the circulation tank 2.
  • the purpose of the partition wall 7 is to prevent a rearwardly directed return flow, schematically illustrated by means of the arrow 8, at the bottom of the circulation tank 2.
  • the rearwardly directed return flow 8 meets the partition wall 7, the same is redirected without having influenced the operation of the aerator section 5.
  • a reaction force is exerted from the partition wall 7 on the waste water, which strengthens the main liquid flow.
  • the partition wall 7 has an upper end 9 that in the vertical direction is situated at a height h that is situated lower than 25 % of the predetermined filling height H of the circulation tank.
  • the upper end 9 of the partition wall 7 in the vertical direction is situated at a height h that is lower than 20 % of the filling height H, more preferably lower than 15 %.
  • a typical height H is in the order of 0,5 m.
  • the partition wall 7 has a lower end 10 that in the vertical direction preferably is situated at a distance 11 from the bottom of the circulation tank 2. It is further preferred that the distance 11 between the lower end 10 of the partition wall 7 and the bottom of the circulation tank 2 is more than 5 cm and less than 15 cm.
  • the purpose of arranging the partition wall 7 with a distance between the lower end 10 of the partition wall 7 and the bottom of the circulation tank 2 is to prevent solid material from being accumulated at the partition wall 7.
  • Figures 3-5 show different embodiments of the partition wall 7 according to the invention.
  • the partition wall 7 has a first surface 12 turned downstream and a second surface 13 opposite the first surface and turned upstream.
  • said first surface 12 is plane; in addition, it is preferred that the first surface 12 is inclined less than 45° in relation to a vertical line.
  • the first surface 12 of the partition wall 7 should be essentially vertical, with the purpose of having as large effective surface as possible in relation to the rearwardly directed return flow 8. It should be appreciated that the partition wall 7 may be divided into several partition wall segments (not shown) arranged beside each other, which may have different mutual angular orientation in relation to a vertical line, with the purpose of optimizing the partition wall 7 in relation to non-uniform rearwardly directed return flow as viewed transversely to the bottom of the circulation tank 2.
  • the second surface 13 of the partition wall 7 may also be plane, like the first surface 12, and is in this case preferably parallel to said first surface 12, according to Figure 3.
  • the second surface 13 may incline in the direction downstream (not shown), i.e., in the direction away from the aerator section 5, preferably less than 45° in relation to a vertical line.
  • the second surface 13 is curved, or non plane, and has some kind of bulging in the upstream
  • FIG. 4 there is shown a curved second surface 13 of the partition wall 7 in the form of a curvature having an arched, or semicircular, cross-section
  • Figure 5 there is shown a curved second surface 13 of the partition wall 7 in the form of a curvature having a triangular, or acute, cross-section. It should be pointed out that the cross-section of the second surface 13
  • the curved shape of the second surface 13 of the partition wall 7 entails that the effect of the partition wall 7 on the main liquid flow 4 can be minimized.
  • the partition wall 7 should be situated at a distance from the aerator section 5.
  • the first surface 12 of the partition wall 7 in the area of the lower end 10 of the partition wall 7 should be situated at a distance 14 from the aerator section 5 that is less than two times the filling height H.
  • said distance should be less than the filling height H, more preferably less than 25 % of the filling height H.

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Activated Sludge Processes (AREA)
  • Physical Water Treatments (AREA)
  • Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Description

TREATMENT PLANT FOR SEWAGE TREATMENT
Technical Field of the Invention
The present invention relates generally to a treatment plant for waste water treatment. In particular, the present invention relates to a treatment plant for biological waste water treatment, the treatment plant comprising a circulation tank, which is arranged to accommodate waste water up to a predetermined filling height, and at least one aerator section arranged at the bottom of the circulation tank. The circulation tank has a predetermined direction of flow along which the waste water is arranged to flow, and the aerator section is arranged to supply gas bubbles to the waste water when the same passes the aerator section. Background of the Invention and Prior Art
A circulation tank, or oxidation ditch, is an open, endless tank that is used in biological purification, or oxidation, of waste water, in which the waste water is brought to flow along the circulation tank and thereby brought to pass different zones in the circulation tank. In such a biological purification, usually the waste water is cleaned from nitrogen and biological material by microorganisms decomposing the biological material into carbon dioxide and water, and bacteria converting the waterborne nitrogen into aerial nitrogen. In case the waterborne nitrogen is not eliminated, this entails the risk of over- fertilization of watercourses and the biological material is strongly oxygen depleting, which gives watercourses
deficient in oxygen, if untreated water is discharged. The decomposition of the biological material is stimulated by the supply of large amounts of oxygen to the waste water, and the elimination of the waterborne nitrogen occurs in areas in the circulation tank without supplied oxygen. Along the circulation tank, there are found at least one so-called aerated zone and at least one so-called non-aerated zone. Accordingly, the above-mentioned aerator section is arranged in the aerated zone.
In one, or a few, aerated zones along the circulation tank, oxygen is added to the waste water by gas bubbles being discharged into the waste water by means of aerator sections arranged at the bottom of the circulation tank. Microorganisms in the so-called activated sludge use the supplied oxygen to decompose the biological material found in the waste water.
Per definition, the waste water should circulate along the circulation tank, and a known attempt to provide a main liquid flow along the circulation tank and to simultaneously obtain uniform aeration of the waste water is disclosed in the withdrawn US patent application 09/801,667. This patent application shows a plant that utilizes the lift of the air in order to create a main liquid flow. The waste water is entered into the aerator section in the vicinity of the bottom of the circulation tank and is discharged on the opposite side of the aerator section in the vicinity of the liquid surface; in this way, the liquid flow and the air flow have more or less the same direction above the aerator section. Accordingly, the main liquid flow is provided by the fact that a first transverse partition wall, arranged upstream the aerator section, extends down into the waste water from above the liquid surface and that a second transverse partition wall, arranged downstream the aerator section, extends up from the bottom of the circulation tank. It is important that the lower end of the first, upper partition wall is on a level that is situated below half the height of the circulation tank, and that the upper end of the second, lower partition wall is on a level that is situated above half the height of the circulation tank. In this way, a liquid flow past the aerator section is created, at the same time as the rise velocity of the air in the waste water is increased. A large disadvantage of the disclosed plant is thus that the supplied air will rise quickly to the surface and leave the waste water. A further disadvantage is that only the upper liquid volume downstream the aerator section will be provided with a flow rate along the circulation tank at the same time as the lower liquid volume will stand still, or recirculate slowly, downstream the aerator section, whereupon the biological material in the waste water risks being accumulated at the bottom of the circulation tank.
In a traditional circulation tank without such partition walls, there is found a strongly rearwardly directed return liquid flow closest to the bottom of the circulation tank, which rearwardly directed return flow is sucked into the aerator section and thereby creates an increased rise velocity of the supplied air. Accordingly, when considering the cross-section of the circulation tank, there are obtained differently directed liquid flows in a cross- section downstream the aerator section, more precisely a high flow rate along the circulation tank in the area of the liquid surface and a rearwardly directed flow at the bottom of the circulation tank.
Brief Description of the Objects of the Invention
The present invention aims at obviating the above- mentioned disadvantages and failings of previously known treatment plants and at providing an improved treatment plant. A primary object of the invention is to provide an improved treatment plant of the initially defined type, which provides a more uniform main liquid flow along the circulation tank when considering a cross-section of the circulation tank downstream the aerator section.
Brief Description of the Features of the Invention
According to the invention, at least the primary object is achieved by the initially defined treatment plant having the features defined in the independent claims. Preferred embodiments of the present invention are furthermore defined in the depending claims.
According to the present invention, a treatment plant of the type initially defined is provided, which is charac- terized in that the same comprises a partition wall arranged transversely to the circulation tank downstream the aerator section, which partition wall has an upper end that in the vertical direction is situated at a height that is lower than 25 % of the predetermined filling height of the circulation tank.
Accordingly, the present invention is based on the understanding that a low partition wall arranged downstream the aerator section stops the rearwardly directed return liquid flow found closest to the bottom of the circulation tank in the area downstream the aerator section, with the purpose of lowering the rise velocity of the air and with the purpose of recovering the linear momentum of the rearwardly directed return flow by means of the reaction force of the partition wall on the waste water, which strengthens the main liquid flow, at the same time as the main liquid flow that passes the aerator section along the circulation tank is affected to an as small as possible extent .
According to a preferred embodiment of the present invention, the upper end of the partition wall in the vertical direction is situated at a height that is less than 20 % of the filling height, preferably less than 15 %.
According to a preferred embodiment, the partition wall has a lower end that in the vertical direction is situated at a distance from the bottom of the circulation tank.
Preferably, the distance between the lower end of the partition wall and the bottom of the circulation tank is more than 5 cm and less than 15 cm. This entails that solid material found in the waste water does not risk being accumulated at the partition wall but can pass freely under the same. Preferably, the partition wall has a first surface turned downstream, which first surface is plane. In a further preferred embodiment, the first surface of the partition wall is essentially vertical. A plane and vertical surface of the partition wall turned downstream gives maximum effective target area in relation to the rearwardly directed return liquid flow with a minimal size of the partition wall. Further, the partition wall has a second surface turned upstream, which second surface is curved in the upstream direction, with the purpose of minimizing the effect on the main liquid flow that passes the aerator section along the circulation tank.
In a further preferred embodiment, the treatment plant comprises at least one flow generating machine arranged upstream said at least one aerator section, which flow generating machine is arranged to generate the main liquid flow along said circulation tank.
Additional advantages and features of the invention are seen in the other dependent claims as well as in the following, detailed description of preferred embodiments.
Brief Description of the Drawings
A more complete understanding of the above-mentioned and other features and advantages of the present invention will be clear from the following, detailed description of preferred embodiments, reference being made to the
accompanying drawings, wherein:
Fig. 1 is a schematic elevated view from above of a treat- ment plant according to the invention,
Fig. 2 is a schematic side view of the aerator section and partition wall of the treatment plant,
Fig. 3 is a schematic cross-sectional view of the partition wall of the treatment plant according to a first embodiment, Fig. 4 is a schematic cross-sectional view of the partition wall of the treatment plant according to a second embodiment, and
Fig. 5 is a schematic cross-sectional view of the partition wall of the treatment plant according to a third embodiment .
Detailed Description of Preferred Embodiments
Reference is initially made to Figures 1 and 2. The present invention relates to a treatment plant, generally designated 1, for waste water treatment comprising
biological material. The treatment plant comprises an endless circulation tank 2, or oxidation ditch, which in the embodiment shown consists of an elongate tank having rounded ends and comprising a centrally placed longitudinal partition 3, whereupon the circulation tank 2 obtains two
parallel and straight channel segments that are connected to each other by two redirecting/semicircular channel segments. It should be pointed out that circulation tanks may have other feasible shapes, for instance an annular shape or a serpentine shape; accordingly, the circulation tank may comprise more straight and redirecting channel segments, respectively, or have an entirely circular/elliptical path shape. The circulation tank 2 is arranged to accommodate waste water up to a predetermined filling height H, even if the actual liquid level in operation may be below as well as exceed said filling height H without the present invention being affected. The waste water is cleaned batch-wise, or continuously, in a treatment plant 1 according to the invention, and with a waste water volume that reaches up to said filling height H, an optimal utilization of the treatment plant 1 is obtained. A typical filling height H is in the order of 3-4 m, but can be as high as 7-8. The circulation tank 2 is arranged with a predetermined direction of flow, schematically illustrated by means of the arrow 4, along which the waste water is intended to flow, while forming a main liquid flow. According to the invention it is of secondary importance how the main liquid flow is
obtained, as long as there is a predetermined direction of flow in the circulation tank 2.
Further, the treatment plant 1 according to the invention comprises at least one aerator section 5 that is arranged in an aerated zone of the circulation tank 2.
Upstream the aerator section 5, there is found a non-aerated zone of the circulation tank 2. In the embodiment shown, the aerator section 5 is arranged in the beginning of a straight channel segment, even if other positions are feasible. Said at least one aerator section 5 is arranged at the bottom of the circulation tank 2 and is arranged to supply oxygen- containing gas bubbles, such as air or pure oxygen, to the waste water, with the purpose of supplying oxygen to the waste water. The aerator section 5 consists, for instance, of a vast number of diffusers or aerator elements, which jointly cover the entire or the main part of the width of the circulation tank 2, a typical width of the circulation tank 2 is in the order of 10-15 m. The length of the aerator section 5 along the circulation tank 2 is in the order of 5- 25 % of the entire length of the circulation tank 2. Preferably, the treatment plant 1 comprises two or more aerator sections 5, which preferably are equidistantly arranged along the circulation tank 2.
In a preferred embodiment, the treatment plant 1 comprises at least one flow generating machine 6 arranged upstream said at least one aerator section 5. The flow generating machine 6 is arranged to generate a flow of waste water along said circulation tank 2, and may consist of one or more so-called slow-moving agitators. Preferably, the treatment plant 1 comprises flow generating machines 6 in two or more positions, which preferably are equidistantly arranged along the circulation tank 2. The treatment plant according to the invention
comprises also at least one partition wall 7 arranged transversely to the circulation tank 2 downstream said at least one aerator section 5. In the description as well as in the appended claims, by the expression "transversely to the circulation tank", reference is made to the fact that the partition wall 7 extends transversely to the direction of flow 4 of the circulation tank 2. Preferably, the partition wall 7 is arranged perpendicular to the direction of flow 4 of the circulation tank 2. The purpose of the partition wall 7 is to prevent a rearwardly directed return flow, schematically illustrated by means of the arrow 8, at the bottom of the circulation tank 2. When the rearwardly directed return flow 8 meets the partition wall 7, the same is redirected without having influenced the operation of the aerator section 5. In other words, a reaction force is exerted from the partition wall 7 on the waste water, which strengthens the main liquid flow.
The partition wall 7 has an upper end 9 that in the vertical direction is situated at a height h that is situated lower than 25 % of the predetermined filling height H of the circulation tank. Preferably, the upper end 9 of the partition wall 7 in the vertical direction is situated at a height h that is lower than 20 % of the filling height H, more preferably lower than 15 %. A typical height H is in the order of 0,5 m.
Further, the partition wall 7 has a lower end 10 that in the vertical direction preferably is situated at a distance 11 from the bottom of the circulation tank 2. It is further preferred that the distance 11 between the lower end 10 of the partition wall 7 and the bottom of the circulation tank 2 is more than 5 cm and less than 15 cm. The purpose of arranging the partition wall 7 with a distance between the lower end 10 of the partition wall 7 and the bottom of the circulation tank 2 is to prevent solid material from being accumulated at the partition wall 7. Now, reference is made primarily to Figures 3-5, which show different embodiments of the partition wall 7 according to the invention. The partition wall 7 has a first surface 12 turned downstream and a second surface 13 opposite the first surface and turned upstream.
According to a preferred embodiment, said first surface 12 is plane; in addition, it is preferred that the first surface 12 is inclined less than 45° in relation to a vertical line. Most preferably, the first surface 12 of the partition wall 7 should be essentially vertical, with the purpose of having as large effective surface as possible in relation to the rearwardly directed return flow 8. It should be appreciated that the partition wall 7 may be divided into several partition wall segments (not shown) arranged beside each other, which may have different mutual angular orientation in relation to a vertical line, with the purpose of optimizing the partition wall 7 in relation to non-uniform rearwardly directed return flow as viewed transversely to the bottom of the circulation tank 2.
The second surface 13 of the partition wall 7 may also be plane, like the first surface 12, and is in this case preferably parallel to said first surface 12, according to Figure 3. Alternatively, the second surface 13 may incline in the direction downstream (not shown), i.e., in the direction away from the aerator section 5, preferably less than 45° in relation to a vertical line. However, it is preferred that the second surface 13 is curved, or non plane, and has some kind of bulging in the upstream
direction. In Figure 4, there is shown a curved second surface 13 of the partition wall 7 in the form of a curvature having an arched, or semicircular, cross-section, and in Figure 5, there is shown a curved second surface 13 of the partition wall 7 in the form of a curvature having a triangular, or acute, cross-section. It should be pointed out that the cross-section of the second surface 13
alternatively may have other shapes than those shown, for instance a polygonal cross-section. The curved shape of the second surface 13 of the partition wall 7 entails that the effect of the partition wall 7 on the main liquid flow 4 can be minimized.
Now, reference is made again to Figure 2. The partition wall 7 should be situated at a distance from the aerator section 5. According to the preferred embodiment, the first surface 12 of the partition wall 7 in the area of the lower end 10 of the partition wall 7 should be situated at a distance 14 from the aerator section 5 that is less than two times the filling height H. Preferably, said distance should be less than the filling height H, more preferably less than 25 % of the filling height H. A rearwardly directed return flow between the partition wall 7 and the aerator section 5 is thereby prevented from being generated.
Feasible Modifications of the Invention
The invention is not limited only to the embodiments described above and shown in the drawings, which only have the purpose of illustrating and exemplifying. This patent application is intended to cover all adaptations and variants of the preferred embodiments described herein, and consequently the present invention is defined by the wording of the accompanying claims and accordingly, the equipment may be modified in all feasible ways within the scope of the accompanying claims.
It should also be pointed out that all information about/regarding terms such as above, below, upper, under, etc., should be interpreted/read with the equipment
orientated in accordance with the figures, with the drawings orientated in such a way that the reference designations can be read in a proper way. Accordingly, such terms only indicate mutual relationships in the shown embodiments, which relationships may be changed if the equipment according to the invention is provided with another construction/design .
It should be pointed out that even if it is not explicitly mentioned that features from one specific embodiment can be combined with the features of another embodiment, this should be regarded as evident when possible.

Claims

Claims
1. Treatment plant for waste water treatment, comprising a circulation tank (2), which is arranged to accommodate waste water up to a predetermined filling height (H) , and at least one aerator section (5) arranged at the bottom of the circulation tank (2), which aerator section (5) is arranged to supply gas bubbles to the waste water, the circulation tank (2) having a predetermined direction of flow along which the waste water is arranged to flow, characterized in that the treatment plant further comprises a partition wall (7) arranged transversely to the circulation tank (2) downstream the aerator section (5), which partition wall (7) has an upper end (9) that in the vertical direction is situated at a height (h) that is lower than 25 % of the above- mentioned filling height (H) .
2. Treatment plant according to claim 1, wherein the upper end (9) of the partition wall (7) in the vertical direction is situated at a height (h) that is lower than 20 % of the filling height (H) , preferably lower than 15 %.
3. Treatment plant according to claim 1 or 2, wherein the partition wall (7) has a lower end (10) that in the vertical direction is situated at a distance from the bottom of the circulation tank (2) .
4. Treatment plant according to claim 3, wherein the distance between the lower end (10) of the partition wall (7) and the bottom of the circulation tank (2) is more than 5 cm and less than 15 cm.
5. Treatment plant according to any one of the preceding claims, wherein the partition wall (7) has a first surface (12) turned downstream, which first surface (12) is plane.
6. Treatment plant according to claim 5, wherein the first surface (12) of the partition wall (7) is inclined less than 45° in relation to a vertical line.
7. Treatment plant according to claim 5 or 6, wherein the first surface (12) of the partition wall (7) is essentially vertical .
8. Treatment plant according to any one of the preceding claims, wherein the partition wall (7) has a second surface (13) turned upstream, which second surface (13) is curved in the upstream direction.
9. Treatment plant according to any one of the preceding claims, wherein the first surface (12) of the partition wall (7) in the area of the lower end (10) of the partition wall (7) is situated at a distance from the aerator section (5), which distance is less than two times the filling height (H) .
10. Treatment plant according to claim 9, wherein the distance between the aerator section (5) and the first surface (12) of the partition wall (7) in the area of the lower end (10) of the partition wall (7) is less than the filling height (H) , preferably less than 25 % of the filling height (H) .
11. Treatment plant according to any one of the preceding claims, wherein the same comprises at least one flow generating machine (6) arranged upstream said at least one aerator section (5), which flow generating machine (6) is arranged to generate a flow of waste water along said circulation tank (2) .
PCT/SE2013/050123 2012-03-28 2013-02-13 Treatment plant for sewage treatment Ceased WO2013147671A1 (en)

Priority Applications (10)

Application Number Priority Date Filing Date Title
US14/389,070 US20150076717A1 (en) 2012-03-28 2013-02-13 Treatment plant for sewage treatment
EP13769485.7A EP2831002A4 (en) 2012-03-28 2013-02-13 Treatment plant for sewage treatment
MX2014010742A MX2014010742A (en) 2012-03-28 2013-02-13 Treatment plant for sewage treatment.
CA2868822A CA2868822A1 (en) 2012-03-28 2013-02-13 Treatment plant for sewage treatment
CN201380017267.5A CN104245600B (en) 2012-03-28 2013-02-13 sewage treatment plant
RU2014143248A RU2014143248A (en) 2012-03-28 2013-02-13 SEWAGE TREATMENT PLANT
HK15102267.5A HK1201810A1 (en) 2012-03-28 2013-02-13 Treatment plant for sewage treatment
KR1020147030084A KR20140138334A (en) 2012-03-28 2013-02-13 Treatment plant for sewage treatment
AU2013240630A AU2013240630B2 (en) 2012-03-28 2013-02-13 Treatment plant for sewage treatment
IN2361KON2014 IN2014KN02361A (en) 2012-03-28 2014-10-27

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
SE1250307-4 2012-03-28
SE1250307A SE536448C2 (en) 2012-03-28 2012-03-28 Wastewater treatment plant

Publications (1)

Publication Number Publication Date
WO2013147671A1 true WO2013147671A1 (en) 2013-10-03

Family

ID=49260772

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/SE2013/050123 Ceased WO2013147671A1 (en) 2012-03-28 2013-02-13 Treatment plant for sewage treatment

Country Status (17)

Country Link
US (1) US20150076717A1 (en)
EP (1) EP2831002A4 (en)
KR (1) KR20140138334A (en)
CN (1) CN104245600B (en)
AR (1) AR090561A1 (en)
AU (1) AU2013240630B2 (en)
CA (1) CA2868822A1 (en)
CL (1) CL2014002548A1 (en)
CO (1) CO7071112A2 (en)
HK (1) HK1201810A1 (en)
IN (1) IN2014KN02361A (en)
MX (1) MX2014010742A (en)
PE (1) PE20142090A1 (en)
RU (1) RU2014143248A (en)
SA (1) SA113340321B1 (en)
SE (1) SE536448C2 (en)
WO (1) WO2013147671A1 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114929633A (en) * 2019-09-19 2022-08-19 赛莱默水处理美国有限公司 System and method for supplying return activated sludge

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107973396A (en) * 2017-08-10 2018-05-01 国电银河水务股份有限公司 It is thoroughly mixed type oxidation trench micro-pore aeration biochemical reactor

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB191400729A (en) * 1914-01-10 1915-01-07 Jones & Attwood Ltd Improvements in Apparatus for the Purification of Sewage or other Impure Waters.
US3884812A (en) * 1973-12-13 1975-05-20 Itt Liquid treatment apparatus
SE516258C2 (en) * 2000-04-14 2001-12-10 Itt Mfg Enterprises Inc Circulation channel for treating sewage or effluent, contains flow barrier for reducing backflow
US20020070164A1 (en) * 2000-12-11 2002-06-13 Huber & Suhner Ag Aeration device for water and a method for aerating water

Family Cites Families (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CH575345A5 (en) * 1974-06-14 1976-05-14 Menzel & Co Activated sludge purificn tanks - ventilated by compressed air, with submerged rotating tube turbines
NL7510116A (en) * 1975-08-27 1977-03-01 Sneek Landustrie DEVICE FOR PURIFICATION OF WASTE WATER.
US5041217A (en) * 1977-11-04 1991-08-20 Reid John H Apparatus for maximizing biological use of entire volume of endless channel in an oxidation ditch
US4902302A (en) * 1977-11-04 1990-02-20 Reid John H Conservation of momentum in a barrier oxidation ditch
DE2839873A1 (en) * 1978-09-13 1980-03-27 Passavant Werke Sewage aeration basin - with cut=outs in partitions for sludge deposit prevention
NL8401713A (en) * 1984-05-29 1985-12-16 Dhv Raadgevend Ing Active sludge effluent water purificn. unit - has oblong open reservoir with central partition to vertical-axis surface aerator propelling the water and partly surrounded by curved wall
US5084167A (en) * 1989-10-23 1992-01-28 Beard Harold J Oxidation ditch for treatment of waste water
US5611926A (en) * 1995-01-13 1997-03-18 Nishida; Tetsuo Water treatment device
AU725812B2 (en) * 1997-06-06 2000-10-19 Norihiko Hirano Method and apparatus for treating wastewater
JP4002851B2 (en) * 2003-04-23 2007-11-07 アタカ大機株式会社 Sewage treatment equipment
US8057674B1 (en) * 2009-01-16 2011-11-15 Ovivo Luxembourg S.{dot over (a)}r.l. Orbital wastewater treatment system and method of operating same
CN101973673A (en) * 2010-10-18 2011-02-16 北京坎普尔环保技术有限公司 Sewage treatment device with aerobic and anoxia reaction regions and film solid-liquid separation region

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB191400729A (en) * 1914-01-10 1915-01-07 Jones & Attwood Ltd Improvements in Apparatus for the Purification of Sewage or other Impure Waters.
US3884812A (en) * 1973-12-13 1975-05-20 Itt Liquid treatment apparatus
SE516258C2 (en) * 2000-04-14 2001-12-10 Itt Mfg Enterprises Inc Circulation channel for treating sewage or effluent, contains flow barrier for reducing backflow
US20020070164A1 (en) * 2000-12-11 2002-06-13 Huber & Suhner Ag Aeration device for water and a method for aerating water

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See also references of EP2831002A4 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114929633A (en) * 2019-09-19 2022-08-19 赛莱默水处理美国有限公司 System and method for supplying return activated sludge
US12497314B2 (en) 2019-09-19 2025-12-16 Xylem Water Solutions U.S.A., Inc. Method for supplying return activated sludge

Also Published As

Publication number Publication date
CL2014002548A1 (en) 2015-07-10
RU2014143248A (en) 2016-05-20
EP2831002A4 (en) 2015-10-07
CO7071112A2 (en) 2014-09-30
CN104245600A (en) 2014-12-24
HK1201810A1 (en) 2015-09-11
AU2013240630B2 (en) 2017-09-14
AR090561A1 (en) 2014-11-19
AU2013240630A1 (en) 2014-11-13
IN2014KN02361A (en) 2015-05-01
CA2868822A1 (en) 2013-10-03
KR20140138334A (en) 2014-12-03
CN104245600B (en) 2016-03-09
SE536448C2 (en) 2013-11-05
PE20142090A1 (en) 2014-12-18
MX2014010742A (en) 2015-02-24
SA113340321B1 (en) 2015-08-12
US20150076717A1 (en) 2015-03-19
EP2831002A1 (en) 2015-02-04
SE1250307A1 (en) 2013-09-29

Similar Documents

Publication Publication Date Title
US8298411B2 (en) System and method for reducing pollution in a body of water
JP2018516753A (en) Nanobubble and hydroxyl radical generator and system for treating sewage without using chemicals using the same
US8110108B2 (en) Wastewater treatment system
US11912586B2 (en) Industrial fish breeding complex and a method of water regeneration
KR101166389B1 (en) Ultra micro-bubble generating Apparatus
US20120067799A1 (en) Water circulation systems with air stripping arrangements for municipal water tanks, ponds, and other potable bodies of water
AU2013240630B2 (en) Treatment plant for sewage treatment
KR100575900B1 (en) Aeration tank with foam removal
US7963508B1 (en) Method and apparatus for digesting sludge
WO2013064742A1 (en) Water treatment plant
US10961140B2 (en) Bioreactor with moving carriers
US7121532B2 (en) Aeration system for liquid
US4202762A (en) Process and device for the aeration of waste water
JP2013022509A (en) Guide plate for impeller and aeration stirring device
JP6845064B2 (en) Water treatment system and how to improve the water treatment system
US2024345A (en) Sewage purifying device
KR101836561B1 (en) Concentrated Organic Waste Water Purifying System
JP3120125U (en) Water purifier
WO2005026063A1 (en) Circular aerator and wastewater treatment apparatus using the same
KR102789203B1 (en) A water treatment apparatus that creates and purifies water flow
WO2014066524A1 (en) Method and apparatus for the treatment of water with a gas or nutrient infused liquid
AU2015282359B2 (en) Aeration entrainment, fractionation and mixing system and a method of using same
KR20220085985A (en) Waste water treatment system with bubbling device
KR20180045459A (en) Apparatus for manufacturing Dissolved oxygen water
EP1884496A2 (en) Ventilation device for an activated sludge tank

Legal Events

Date Code Title Description
WWE Wipo information: entry into national phase

Ref document number: 201380017267.5

Country of ref document: CN

121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 13769485

Country of ref document: EP

Kind code of ref document: A1

WWE Wipo information: entry into national phase

Ref document number: MX/A/2014/010742

Country of ref document: MX

WWE Wipo information: entry into national phase

Ref document number: 14203774

Country of ref document: CO

WWE Wipo information: entry into national phase

Ref document number: 2014002548

Country of ref document: CL

Ref document number: P1026/2014

Country of ref document: AE

ENP Entry into the national phase

Ref document number: 2868822

Country of ref document: CA

WWE Wipo information: entry into national phase

Ref document number: 001486-2014

Country of ref document: PE

NENP Non-entry into the national phase

Ref country code: DE

WWE Wipo information: entry into national phase

Ref document number: 2013769485

Country of ref document: EP

Ref document number: 14389070

Country of ref document: US

REG Reference to national code

Ref country code: BR

Ref legal event code: B01A

Ref document number: 112014024162

Country of ref document: BR

ENP Entry into the national phase

Ref document number: 20147030084

Country of ref document: KR

Kind code of ref document: A

ENP Entry into the national phase

Ref document number: 2014143248

Country of ref document: RU

Kind code of ref document: A

ENP Entry into the national phase

Ref document number: 2013240630

Country of ref document: AU

Date of ref document: 20130213

Kind code of ref document: A

ENP Entry into the national phase

Ref document number: 112014024162

Country of ref document: BR

Kind code of ref document: A2

Effective date: 20140929