GB2317168A - Sequential batch reactor - Google Patents

Sequential batch reactor Download PDF

Info

Publication number
GB2317168A
GB2317168A GB9619089A GB9619089A GB2317168A GB 2317168 A GB2317168 A GB 2317168A GB 9619089 A GB9619089 A GB 9619089A GB 9619089 A GB9619089 A GB 9619089A GB 2317168 A GB2317168 A GB 2317168A
Authority
GB
United Kingdom
Prior art keywords
tank
sewage
aerobic digestion
effluent
batch reactor
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.)
Granted
Application number
GB9619089A
Other versions
GB2317168B (en
GB9619089D0 (en
Inventor
James Redfern Brown
Robert Kenneth Oram
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.)
Balmoral Group Ltd
Original Assignee
Balmoral Group 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
Application filed by Balmoral Group Ltd filed Critical Balmoral Group Ltd
Priority to GB9619089A priority Critical patent/GB2317168B/en
Publication of GB9619089D0 publication Critical patent/GB9619089D0/en
Priority to GB9719518A priority patent/GB2317170B/en
Publication of GB2317168A publication Critical patent/GB2317168A/en
Application granted granted Critical
Publication of GB2317168B publication Critical patent/GB2317168B/en
Anticipated expiration legal-status Critical
Expired - Fee Related 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
    • C02F3/1236Particular type of activated sludge installations
    • C02F3/1263Sequencing batch reactors [SBR]
    • 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
    • C02F3/1242Small compact installations for use in homes, apartment blocks, hotels or the like
    • 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

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)

Abstract

A sequential batch reactor comprises a rotationally moulded settlement tank 1, an aerobic digestion tank 13 received within the settlement tank and means to transfer sewage (i) into the settlement tank, (ii) from the settlement tank to the digestion tank and (iii) away from the digestion tank. Preferably the reactor also has a transfer compartment 17 between the settlement tank and digestion tank, the transfer compartment having holes which prevent gross solids from entering. In use, effluent is introduced into the settlement tank 1 via pipe 10, some of the effluent transfers to compartment 17, an airlift pump 20 is periodically activated so as to transfer an aliquot of sewage into the digestion tank 13 and, once treated, the sewage is transferred away via outlet 23 to a drain or sewage system.

Description

SEQUENTIAL BATCH REACTOR This invention relates to a sequential batch reactor for use in treating sewage.
According to the invention there is provided a sequential batch reactor comprising a primary settlement tank having an inlet for introducing effluent into the reactor, an aerobic digestion tank received in the primary settlement tank and having an outlet for transferring digested effluent from the reactor, means for transferring effluent from the primary settlement tank to the aerobic digestion tank and means for transferring treated effluent from the aerobic digestion tank to a drain or sewage system.
Embodiments of the invention will be illustrated by way of non-limiting example to the figures of which: Figure 1 is a cross-sectional view; and Figure 2 is a perspective view of a section of a further embodiment.
The illustrated embodiments comprise a broadly spherical tank 1 having body 2 provided with flat base 3 with a punt 3a and a cylindrical neck 4.
Conveniently tank 1 is rotationally moulded since this allows the tank to be made without an equatorial seam which could leak. The invention is not to be construed as restricted to rotationally moulded tanks. Those skilled in the art will have little difficulty in manufacturing the tank body in other ways for example from glass fibre reinforced plastics material.
In the illustrated embodiment neck 4 is provided with extension piece 6 terminating in access cover 7. An inwardly directed flange 8 of the extension piece 6 abuts inwardly directed flange 9 of the neck 4.
The tank is further provided with an inlet 10 having an upwardly extended member 11 and a downwardly directed member 12.
A digestor tank 13 is received in the body 2 of tank 1. Digestor tank 13 is generally cylindrical and may stand on the base 3 and punt 3a of tank 1. As will become apparent hereinafter it may be desirable to provide a deflector 14 in the digestor tank. This can conveniently be formed in the digestor tank if it too is a rotational molding. In the illustrated embodiment the upper part 16 of the digest or tank is of lesser diameter than the lower.
A compartment 17 is in the illustrated embodiment provided in the tank 1 and defined by walls 18 and 19. This is not essential. Once more the compartment is desirably a rotationally molded product. Holes (not shown) are provided in compartment 17 to allow liquid to flow from the tank into the compartment 17.
A conduit allowing controlled transfer of liquid from the compartment 17 into the digestor tank is provided. In the illustrated embodiment this comprises an airlift pump 20 and pipe 21. A remote compressor (not shown) supplies air to the airlift pump. While an airlift pump is not essential for the performance of the invention it is desirable. In principle other pumps such as immersed mains pumps could be used as could bucket devices and centrifugal pumps. In practice however an air lift pump is advantageous since no moving parts or mains voltage need be present. Reliability and safety can thereby be improved.
Digestor tank 13 is provided with an aerator 22 for passing air bubbles through liquid contained in the digestor tank. Aerator 22 can be supplied by the same compressor as the pump.
A discharge conduit allowing controlled transfer of liquid from the digestor tank to outlet 23 is also provided. The discharge conduit conveniently comprises a pipe 24 and a further airlift pump (not shown).
Typical operation of the device will now be described. Waste enters the tank body through the inlet 10. The outer tank body 2 functions as a primary settlement tank which is to say that solids settle out into the base. After continued operation (typically a year) the accumulated solids may be drawn out by suction hose through either extension piece 11 and 12 or directly, with the reduced diameter portion of the digestor tank facilitating the introduction of a pipe for removal of the solids.
Typically discharge into the tank shows a wide variation in now rate. For example in the early morning and early evening large quantities of effluent are produced by the flushing of lavatories and so forth. In the middle of the night little effluent is discharged. Tank 1 also serves to provide a buffer. In the event of major overload for example due to malfunction liquid will back-up the inlet 10 thereby raising the alarm but will not be discharged through the outlet 23. It may however be covenient to provide an emergency overflow from the outer tank. In some cases anaerobic digestion of the effluent occurs in the tank 1. This is desirable but not essential.
Some of the effluent contained in tank 1 transfers to compartment 17 where fitted. The holes in the compartment wall prevent gross solids from entering the compartment.
At intervals the airlift pump 20 is activated and transfer an aliquot to the digestor tank 13. The level in tank 1 thus falls in preparation for further effluent.
The airlift pump can be controlled by a simple time switch. It is preferred however to employ a programmable logic controller (PLC) so that if there is little or no flow into the device a small transfer only into the digestor occurs so that sufficient nutrients to prevent die back of the micro-organisms contained in the digestor are transferred.
Material in the digestor tank is aerated optionally under timer or PLC control. The combination of nutrients in the effluent and introduced oxygen cause resident microorganisms to degrade the effluent. After a relatively short time typically 6 to 12 hours the suspended solids content and biological oxygen demand (BOD) of the liquor after settlement are dramatically reduced. For example in a trial after stabilisation a reactor of the invention produced product of 10 mg/m3 suspended solids and 10 mg/m3 BOD as compared to a commercially available device which achieved 30 mg/m3 suspended solids and 20 mg/m3 BOD.
At the end of the aerobic digestion and settlement process the clarified and digested effluent is transferred to the outlet 23 leaving an inoculum in the digestor tank 13. Deflector 14 serves to cause mixing of the effluent as it is pumped out thereby ensuring that treated effluent from throughout the tank is withdrawn.
In the event the outlet 23 becomes blocked or some other malfunction occurs the digestor tank fills. When flill it overflows into the tank 1 thereby reducing the likelihood of environmental damage. The resting of the tanks has further advantages. Liquid contained in the outer tank 1 helps maintain the liquid in the digestor at a constant temperature. A more compact installation than those in which the primary settlement/aerobic digestion tank is separate from the aerobic digestion tank. The amount of in soil pipework required in accordance with the invention is reduced and thus the likelihood of damage if the ground is disturbed is reduced. The aerobic digestion tank can be of lighter, and hence cheaper, construction than a separate one which must be designed to tolerate the full local soil loadings.

Claims (11)

Claims
1. A sequential batch reactor comprising a primary settlement tank having an inlet for introducing effluent into the reactor, an aerobic digestion tank received in the primary settlement tank and having an outlet for transferring digested effluent from the reactor, means for transferring effluent from the primary settlement tank to the aerobic digestion tank and means for transfering treated effluent from the aerobic digestion tank to a drain or sewage system.
2. A sequential batch reactor as claimed in claim 1 further comprising a transfer compartment intermediate the primary settlement tank and the aerobic digestion tank.
3. A sequential batch reactor as claimed in claim 1 or claim 2 wherein at least one of the primary settlement tank, the aerobic digestion tank and the transfer compartment when present are rotational molded.
4. A sequential batch reactor substantially as hereinbefore described by reference to Figure 1.
5. A sequential batch reactor substantially as hereinbefore described by reference to Figure 2.
6. A method of treating sewage comprising the steps of a introducing the sewage into a primary settlement tank b transferring an aliquot of sewage from the primary settlement tank to an aerobic digestion tank received in the primary settlement tank, c subjecting the aliquot to aerobic digestion so as to obtain a treated sewage and d transferring the treated sewage from the aerobic digestion tank.
7. A method as claimed in claim 6 wherein the sewage is transferred by an airlift pump.
8. A method as claimed in claim 6 or claim 7 wherein intermediate steps a and b the sewage gross solids are filtered from the sewage.
9. A method of treating sewage substantially as hereinbefore described by reference to Figure 1.
10. A method of treating sewage substantially as hereinbefore described by reference to Figure 2.
Amendments to the claims have been fled as follows 1. A sequential batch reactor comprising a rotationally molded primary settlement tank having an inlet for introducing effluent into the reactor; an aerobic digestion tank received in the primary settlement tank and having an outlet for transferring digested effluent from the reactor, means for transferring effluent from the primary settlement tank to the aerobic digestion tank and means for transferring treated effluent from the aerobic digestion tank to a drain or sewage system.
2. A sequential batch reactor as claimed in claim 1 further comprising a transfer compartment intermediate the primary settlement tank and the aerobic digestion tank.
3. A sequential batch reactor as claimed in claim 2 wherein the transfer compartment is rotationally molded.
4. A sequential batch reactor as claimed in any one of claims I to 3 wherein the transfer compartment is rotationally molded.
5. A sequential batch reactor substantially as hereinbefore described by reference to Figure 1.
6. A sequential batch reactor substantially as hereinbefore described by reference to Figure 2.
7. A method of treating sewage comprising the steps of a introducing the sewage into a rotationally molded primary settlement tank b transferring an aliquot of sewage from the primary settlement tank to an aerobic digestion tank received in the primary settlement tank; c subjecting the aliquot to aerobic digestion so as to obtain a treated sewage and d transferring the treated sewage from the aerobic digestion tank.
8. A method as claimed in claim 7 wherein the sewage is transferred by an airlift pump.
9. . A method as claimed in claim 7 or claim 8 wherein intermediate steps a and b the sewage gross solids are filtered from the sewage.
10. A method of treating sewage substantially as hereinbefore described by reference to Figure 1.
11. A method of treating sewage substantially as hereinbefore described by reference to Figure 2.
GB9619089A 1996-09-12 1996-09-12 Sequential batch reactor Expired - Fee Related GB2317168B (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
GB9619089A GB2317168B (en) 1996-09-12 1996-09-12 Sequential batch reactor
GB9719518A GB2317170B (en) 1996-09-12 1997-09-12 Sequential batch reactor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
GB9619089A GB2317168B (en) 1996-09-12 1996-09-12 Sequential batch reactor

Publications (3)

Publication Number Publication Date
GB9619089D0 GB9619089D0 (en) 1996-10-23
GB2317168A true GB2317168A (en) 1998-03-18
GB2317168B GB2317168B (en) 1998-11-04

Family

ID=10799847

Family Applications (2)

Application Number Title Priority Date Filing Date
GB9619089A Expired - Fee Related GB2317168B (en) 1996-09-12 1996-09-12 Sequential batch reactor
GB9719518A Expired - Fee Related GB2317170B (en) 1996-09-12 1997-09-12 Sequential batch reactor

Family Applications After (1)

Application Number Title Priority Date Filing Date
GB9719518A Expired - Fee Related GB2317170B (en) 1996-09-12 1997-09-12 Sequential batch reactor

Country Status (1)

Country Link
GB (2) GB2317168B (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0893413A1 (en) * 1997-07-17 1999-01-27 Franz Carl Nüdling Basaltwerke GmbH & Co. KG Process and device for the biological treatment of liquids, in particular for the complete biological clarification of waste water
EP1031540A1 (en) * 1999-02-25 2000-08-30 Markus Baumann Apparatus for water treatment
EP1300367A2 (en) * 2001-10-05 2003-04-09 Markus Baumann Small installation for the treatment of wastewater
EP1388524A1 (en) * 2002-08-06 2004-02-11 RHEBAU Rheinische Beton- und Bauindustrie GmbH & Co. Discontinuous sewage treatment process and small installation for carrying out this process
WO2005030656A1 (en) * 2003-09-26 2005-04-07 Otv Sa Improvements relating to water treatment apparatus
EP1612191A1 (en) 2004-07-02 2006-01-04 Gerd Bednarsch Fully biological sewage treatment installation according to the SBR process with the reactor integrated in the preclarification tank

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FI117141B (en) * 2003-02-21 2006-06-30 Uponor Innovation Ab Sewage treatment plant and sewage well
GB0724813D0 (en) 2007-12-20 2008-01-30 Questor Technologies Ltd Improvements relating to water treatment
WO2009128765A1 (en) * 2008-04-17 2009-10-22 Phytotechnology Europe Ab A phytosystem for treatment of sewage
EP2345766B1 (en) * 2010-01-13 2017-07-26 Uponor Infra Oy Waste liquid tank
DE202016008244U1 (en) 2016-07-12 2017-07-25 Delphin Water Systems Gmbh & Co. Kg Tank for a small sewage treatment plant

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3966608A (en) * 1974-03-01 1976-06-29 Ecodyne Corporation Liquid treatment apparatus
US5156742A (en) * 1992-02-25 1992-10-20 Smith & Loveless, Inc. Liquid treatment method and apparatus
GB2275921A (en) * 1993-03-12 1994-09-14 John Laurence Nicholson Sewage treatment plant

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB8713211D0 (en) * 1987-06-05 1987-07-08 Secr Defence Sewage treatment plant
US5647986A (en) * 1994-12-02 1997-07-15 Nawathe; Dilip Apparatus and process for distributed treatment of wastewater

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3966608A (en) * 1974-03-01 1976-06-29 Ecodyne Corporation Liquid treatment apparatus
US5156742A (en) * 1992-02-25 1992-10-20 Smith & Loveless, Inc. Liquid treatment method and apparatus
GB2275921A (en) * 1993-03-12 1994-09-14 John Laurence Nicholson Sewage treatment plant

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0893413A1 (en) * 1997-07-17 1999-01-27 Franz Carl Nüdling Basaltwerke GmbH & Co. KG Process and device for the biological treatment of liquids, in particular for the complete biological clarification of waste water
EP1031540A1 (en) * 1999-02-25 2000-08-30 Markus Baumann Apparatus for water treatment
EP1300367A2 (en) * 2001-10-05 2003-04-09 Markus Baumann Small installation for the treatment of wastewater
EP1300367A3 (en) * 2001-10-05 2004-02-11 Markus Baumann Small installation for the treatment of wastewater
EP1388524A1 (en) * 2002-08-06 2004-02-11 RHEBAU Rheinische Beton- und Bauindustrie GmbH & Co. Discontinuous sewage treatment process and small installation for carrying out this process
WO2005030656A1 (en) * 2003-09-26 2005-04-07 Otv Sa Improvements relating to water treatment apparatus
EP1612191A1 (en) 2004-07-02 2006-01-04 Gerd Bednarsch Fully biological sewage treatment installation according to the SBR process with the reactor integrated in the preclarification tank

Also Published As

Publication number Publication date
GB2317170A (en) 1998-03-18
GB2317168B (en) 1998-11-04
GB9719518D0 (en) 1997-11-19
GB9619089D0 (en) 1996-10-23
GB2317170B (en) 2000-03-29

Similar Documents

Publication Publication Date Title
US4325823A (en) Wastewater treatment system
US3844946A (en) Aerobic wastewater treatment system with partial reuse and infrequent dosing to soil
US3920550A (en) Process and equipment for automatic chemical-biological wastewater treatment with provisions for recycle and reuse
US5609754A (en) Secondary sewage treatment system
US3875051A (en) Sewage treatment system
US5186821A (en) Wastewater treatment process with cooperating velocity equalization, aeration and decanting means
CA2206744A1 (en) Apparatus and process for distributed treatment of wastewater
US3834536A (en) Aerobic wastewater treatment apparatus
CA2216958A1 (en) Method and apparatus for treating waste water
GB2317168A (en) Sequential batch reactor
WO2007089168A1 (en) Self-regulatng method for sewage water treatment and a device for carrying out said method
EP0031332B1 (en) Waste disposal apparatus
CZ300894A3 (en) Waste or sewage water treatment by combining continuous and discontinuous through flow
KR100372601B1 (en) Food sweeping treatment system
SK283582B6 (en) Reactor for biological sewage purification
EP1136449B1 (en) Waste water processing system
US3709363A (en) Extended aeration, activated sludge plant
US3746638A (en) Batch sewage treatment system and method
GB2224728A (en) Sewage treatment plant
KR101971057B1 (en) spontaneous-floating type decanter with a function of adjusting buoyancy and sequencing batch reactor type wastewater treatment method using the same
US7169306B1 (en) Versatile pre-thickened aerobic digester system
KR100470175B1 (en) Floating Mixture Decanter
KR100404668B1 (en) System for control drain water
US2274953A (en) Sludge digester
GB2053885A (en) Waste disposal apparatus

Legal Events

Date Code Title Description
PCNP Patent ceased through non-payment of renewal fee

Effective date: 20130912