CA2631906A1 - Versatile biological wastewater treatment system - Google Patents
Versatile biological wastewater treatment system Download PDFInfo
- Publication number
- CA2631906A1 CA2631906A1 CA 2631906 CA2631906A CA2631906A1 CA 2631906 A1 CA2631906 A1 CA 2631906A1 CA 2631906 CA2631906 CA 2631906 CA 2631906 A CA2631906 A CA 2631906A CA 2631906 A1 CA2631906 A1 CA 2631906A1
- Authority
- CA
- Canada
- Prior art keywords
- aeration
- chamber
- aerated
- wastewater
- activated sludge
- 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.)
- Abandoned
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
- C02F3/308—Biological phosphorus removal
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/12—Activated sludge processes
- C02F3/1278—Provisions for mixing or aeration of the mixed liquor
- C02F3/1294—"Venturi" aeration means
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/105—Phosphorus compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
- C02F2101/163—Nitrates
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
- C02F2101/166—Nitrites
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/001—Upstream control, i.e. monitoring for predictive control
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/10—Solids, e.g. total solids [TS], total suspended solids [TSS] or volatile solids [VS]
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/38—Gas flow rate
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/40—Liquid flow rate
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
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)
- Health & Medical Sciences (AREA)
- Molecular Biology (AREA)
- Activated Sludge Processes (AREA)
Abstract
A versatile and efficient biological wastewater treatment system is provided which is adaptable to small, shop fabricated package plants and large, assembled in place plants, and which can be operated as a secondary treatment, activated sludge process, for suspended solids and Biochemical Oxygen Demand (BOD) removal, or a tertiary treatment, activated sludge process, for suspended solids, Biological Oxygen Demand (BOD), Nitrogen and Phosphorous removal. The system major equipment includes a wastewater pump and an air aspirator-mixer to provide aeration, sludge recirculation and waste, and wastewater recirculation for the secondary and tertiary treatment processes.
The aeration system with the air aspirator-mixer is highly efficient in oxygen transfer to the wastewater, easy to maintain and versatile to use, as it is located outside aeration tanks. The wastewater pump and air aspirator-mixer system lends itself to continuous and cyclic aeration and oxic and anoxic treatment processes. The multiple use of the wastewater pump for aeration, recirculation and sludge waste minimizes the number of pumping systems required and eliminates air blowers.
The aeration system with the air aspirator-mixer is highly efficient in oxygen transfer to the wastewater, easy to maintain and versatile to use, as it is located outside aeration tanks. The wastewater pump and air aspirator-mixer system lends itself to continuous and cyclic aeration and oxic and anoxic treatment processes. The multiple use of the wastewater pump for aeration, recirculation and sludge waste minimizes the number of pumping systems required and eliminates air blowers.
Description
J.K. FILE NO: 100WWT
Field of the Invention The invention relates to a process and apparatus for biological wastewater treatment as a secondary or a tertiary treatment process.
Background of the Invention Biological, activated sludge wastewater treatment process usually operates as a secondary treatment system or a tertiary treatment system for removal of Suspended Solids, Biochemical Oxygen Demand, Nitrogen and/or Phosphorous.
The treatment systems involve wastewater aeration, sludge recirculation and disposal (waste) and aerated wastewater recirculation. The aeration system can be continuous or cyclic. The aeration system usually requires air blowers and air diffusers located in aeration tanks or proprietary air aspirators are used in conjunction with a pump which pumps wastewater and air in an aeration chamber.
Simple one-pump aeration system usually operates as a secondary treatment process with a sludge recirculation or extended aeration secondary treatment process without a sludge recirculation. These processes do not provide a tertiary treatment and the secondary treatment which they provide is not well controlled and efficient. These systems usually require large tanks to provide adequate secondary treatment due to a lack of an adequate treatment process and controls in regard to sludge recirculation and disposal of excess sludge, and aeration and mixing in the aeration chamber, and recirculation of aerated wastewater.
J.K. FILE NO: 100WWT
Also, the aeration systems used are not efficient in regard to the oxygen transfer to the wastewater.
This invention is based on the wastewater aeration by means of a pump and an efficient air aspirator-mixer. The pump also recirculates and wastes the sludge produced by the biological treatment process, and recirculates the aerated wastewater to accomplish a tertiary treatment. The air aspirator-mixer is highly efficient in regard to the oxygen transfer to the wastewater.
The objectives of this invention include the following:
= To provide wastewater aeration, sludge recirculation and waste and wastewater recirculation by means of the same pump.
= To supply air to the wastewater and sludge and to mix the air and the wastewater and sludge by an efficient air aspirator-mixer.
= To provide a tertiary biological wastewater treatment process for removal of Suspended Solids, Biochemical Oxygen Demand, Nitrogen and Phosphorous and which can also be used as a secondary biological wastewater treatment for removal of Suspended Solids and Biochemical Oxygen Demand.
= To provide flexibility and control of the time and rates of the wastewater and sludge aeration, sludge recirculation and waste, and the aerated wastewater recirculation.
J.K. FILE NO: 100WWT
= To provide wastewater treatment system which can be used for small, shop fabricated treatment plants for installation above or under ground, and large, site assembled treatment plants.
= To provide wastewater treatment system which is compact and has a small foot print.
= To provide a system of low operation and maintenance requirements.
Summary of the Invention The treatment system of the present invention is a process and apparatus for biological, activated sludge treatment of municipal and industrial wastewaters.
The treatment system provides a tertiary treatment for removal of Suspended Solids, Biochemical Oxygen Demand, Nitrogen and Phosphorous. Also, the treatment system can operate as a secondary treatment for removal only of Suspended Solids and Biochemical Oxygen Demand.
The treatment system comprises primary suspended solids and excess (waste) activated sludge retention chamber, anoxic chamber, aeration chamber, clarifier chamber, wastewater aeration and recirculation, activated sludge recirculation, aeration and waste system, and instrumentation as shown on Fig. 1& 2.
A wastewater pump and an efficient air aspirator-mixer are used to provide the wastewater aeration and recirculation, and the activated sludge recirculation, aeration and waste. The wastewater pump can be a submersible pump located in the aeration chamber J.K. FILE NO: 100WWT
or a dry pit pump located beside the aeration chamber. The air aspirator-mixer is located either above or beside the aeration chamber. Single or multiple pumps and air aspirator-mixers can be used, depending on the size and capacity of the treatment system.
A wastewater effluent pump can be used instead of a non-clog wastewater pump for a better efficiency of the pumping and aeration process.
The patented J.K. air aspirator-mixer (Patent No. US 6,969,052 B2) is preferred, but other air aspirators and mixers can be used as well, if adequate air supply and the air and wastewater mixing are provided.
The primary suspended solids and the excess activated sludge retention chamber is sized either to retain the sludge for a longer period of time of several months or weeks, which may be preferred in small treatment systems, such as domestic or institutional systems, or for a much shorter period of time of several hours or days which is preferred in large treatment systems such as municipal or large industrial systems, in which case, the sludge is removed from the chamber continuously or intermittently daily for further treatment or disposal.
The aeration process can be continuous or intermittent depending on the wastewater supply pattern throughout a day or other period of time.
In the continuous aeration mode, it is preferred to control the air supply flow rate such to develop horizontal stratification zones in the aeration chamber, from the bottom to the top, of a high aeration zone, a moderate aeration zone, a light aeration zone and a J.K. FILE NO: 100WWT
mixed anoxic zone, in order to continuously provide Biochemical Oxygen Demand removal, nitrification and denitrification in the aeration chamber.
The wastewater and activated sludge are also recirculated to the anoxic chamber, located between the primary sludge holding chamber and the aeration chamber, in order to provide for phosphorous and nitrogen removal in the anoxic chamber.
In the anoxic chamber, the aerated wastewater and activated sludge are mixed with the fresh unaerated wastewater which quickly depletes the oxygen contained in the aerated wastewater, thus phosphorous and nitrogen removal processes are accomplished.
In the intermittent aeration mode, the wastewater is subjected to aeration and no aeration (anoxic) with mixing periods of approximately 1 hour to 2 hours each period.
The wastewater is recirculated to the anoxic chamber during the aeration period or both during the aeration and no-aeration periods. The intermittent aeration mode is preferred during low wastewater flow periods and no flow periods which may appear in small systems or industrial systems operated on shift basis, and low strength wastewater systems.
The use of the highly efficient air aspirator-mixer, patented by the inventor, ensures a high level of oxygen transfer to the wastewater immediately after the air is aspired into and mixed with the wastewater, and which takes place before the aerated waste water enters the aeration chamber. The oxygen transfer into the wastewater continues in the aeration chamber but it diminishes from the bottom to the top of the J.K. FILE NO: 100WWT
chamber, thus the level of aeration (oxygen transfer) is reduced from the bottom to the top and the horizontal aeration stratification zones are developed in the aeration chamber.
The other advantage is derived from the aeration stratification, that the inlet unaerated wastewater and the activated sludge return from the clarifier are mixed with the highly aerated wastewater and the mixture is further immediately re-aerated and mixed in the air aspirator-mixer and returned to the highly aerated wastewater zone.
The aeration and recirculation pump provides the aeration and recirculation of the wastewater, and the activated sludge at a flow rate of up to twelve times higher than the inlet wastewater design flow rate. The activated sludge recirculation flow rate and the aerated wastewater flow rate are several times higher than the inlet wastewater flow rate and up to 70% of the aeration/recirculation pump flow rate. The flow rates are related to the inlet wastewater quality and the required treated effluent quality.
The aerated wastewater flows into the clarifier at a flow rate of up to 100%
higher than the inlet wastewater design flow rate. The biomass developed in the aeration process settles at the bottom of the clarifier and is recirculated to the aeration chamber along with a portion of the treated wastewater which entered the clarifier.
The portion of the treated and clarified wastewater, equal to the inlet wastewater flow rate, is discharged from the clarifier to a disposal.
The activated sludge is intermittently or continuously wasted into the primary suspended solids and excess activated sludge retention chamber by intermittent or J.K. FILE NO: 100WWT
continuous discharges of the recirculated wastewater and activated sludge into the sludge retention chamber.
A portion of the wastewater and activated sludge recirculated by the aeration and recirculation pump is discharged to the upper zone in the aeration chamber, before the wastewater and activated sludge are re-aerated, to provide nutrients for the denitrification process which takes place in the upper part of the aeration chamber.
A suspended solids meter is preferred to monitor the suspended solids (mixed licquir suspended solids) density in the aeration chamber lower, high aeration zone and dissolved oxygen meters are preferred to monitor the dissolved oxygen in the aeration chamber lower, high aeration zone and the upper, low aeration/anoxic zone boundary.
A flow meter is preferred on the inlet wastewater line to monitor the inlet wastewater flow rates and volumes.
The above instrumentation is not mandatory, but it is preferred to facilitate setting up of the system operating parameters for a high efficiency performance, reliability and consistency in applications of varying inlet wastewater flow rates and quality.
Brief Descriptions of the Drawings Having thus generally described the invention, it will be referred to more specifically by reference to the accompanying drawings illustrating preferred embodiments, and in which:
J.K. FILE NO: 100WWT
Fig. 1 is a diagrammatic illustration in vertical cross-section of the treatment process and apparatus with the aeration and recirculation pump located inside the aeration chamber.
Fig. 2 is a diagrammatic illustration in horizontal cross-section of the treatment process and apparatus with the aeration and recirculation pump located inside the aeration chamber.
Detailed Description of the Invention According to the embodiment of the invention, as shown on Fig. 1& 2, the treatment system comprises the following major components: a primary suspended solids and activated sludge waste retention chamber 1, further referred to as retention chamber, an anoxic chamber 2, an aeration chamber 3, a clarifier chamber 4, access manholes 5, an inlet wastewater pipe 7, an inlet wastewater flow meter 8, an aeration and recirculation pump 28, an air aspirator-mixer 34, and an effluent wastewater pipe 47.
Inlet wastewater enters the retention chamber 1 through the inlet pipe 7, the flow meter 8 and a discharge pipe 9. The flow meter 8 is vented on the inlet and outlet sides with vent pipes 10. The discharge pipe 9 is preferably directed toward the front end of the retention chamber 1.
The inlet wastewater suspended solids and the activated waste sludge settle in the retention chamber 1 and a clarified wastewater flows toward the anoxic chamber 2, as shown by a flow direction arrow 11.
J.K. FILE NO: 100WWT
The clarified wastewater flows to an overflow trough 13 and further to the anoxic chamber 2, through a pipe 14 which connects to a wastewater and activated sludge return pipe 38, inside the anoxic chamber 2.
The clarified wastewater and recirculated wastewater and activated sludge mix together in the anoxic chamber 2 and the mixture of the wastewater and the activated sludge flows to the aeration and recirculation pump 28 through a perforated pipe 16 located in the anoxic chamber 2 and a perforated pipe 17 (single or multiple) located in the aeration chamber 3.
The aeration and recirculation pump 28 receives wastewater and activated sludge from the anoxic chamber 2, aerated wastewater from the bottom of the aeration chamber 3 and nitrified and partially denitrified wastewater from the top of the aeration chamber 3, and activated sludge from the clarifier chamber 4.
The mixture of wastewater and activated sludge is pumped into two streams;
one, an aeration stream through a pipe 33 and the air aspirator-mixer 34 where it mixes with air and the aerated mixture is discharged into the aeration chamber 3 through solid discharge pipe 35 and bottom perforated pipe 36, and the second, a recirculation stream, through a pipe 37, is not aerated and it is occasionally or continuously discharged to the retention chamber 1 through a control valve 41 and a discharge pipe 39 and to the anoxic chamber 2 through a control valve 40 and a discharge pipe 38, and to the upper part of the clarifier 3 through a control valve 55 and a discharge pipe 54.
J.K. FILE NO: 100WWT
Treated wastewater and activated sludge overflow from the aeration chamber 3 into the clarifier chamber 4 through horizontal troughs 27 and discharge pipes 26 & 25.
The discharge pipe 25 is provided with a non-return valve to prevent flow of the treated wastewater from the upper part of the clarifier chamber 4 to the aeration and recirculation pump 28.
The treated wastewater and the activated sludge separate in the clarifier chamber 4 and a clarified treated wastewater overflows to a trough 46 and further to the effluent pipe 47, and the activated sludge settles to the bottom of the clarifier chamber 4, and it is returned by the aeration and recirculation pump 28 partially to the aeration chamber 3, anoxic chamber 2 and the retention chamber 1 where the activated sludge is wasted.
The treatment processes which take place in the aeration chamber 3 comprise four horizontal zones which from the bottom to the top are high aeration, moderate aeration, low aeration and anoxic zone.
The Biochemical Oxygen Demand (BOD) removal and the nitrification of ammonia to nitrate take place in the high, moderate and low aeration zones while the denitrification process takes place in the anoxic zone.
The nitrified and partially denitrified wastewater which is returned to the anoxic chamber 2 undergoes a phosphorous removal process and further denitrification process.
A suspended solids removal is accomplished in the retention chamber 1 and in the clarifier chamber 4.
J.K. FILE NO: 100WWT
The aeration system which comprises the aeration and recirculation pump 28 and the air aspirator-mixer 34 also includes an open/close control valve 44, a rotometer 43 and an air inlet pipe 42. The rotometer 43 measures the air flow rate and the control valve 44 permits to operate the aeration chamber 3 in intermittent modes of aeration and no aeration (anoxic) while maintaining mixing of the wastewater in the aeration chamber 3 by the aeration and recirculation pump 28. This mode of operation is preferred during low flow or no flow of the inlet wastewater periods, and low strength wastewater systems.
Wastewater & activated sludge mixture flow rates into the aeration stream 33 and the recirculation stream 37, can be adjusted by manually operated valves 31 &
32.
The density of the suspended solids in the aeration chamber 3 is monitored by a suspended solids meter 52 and the desired density of the suspended solids in the aeration chamber 3 is maintained by periodical discharges of the mixture of the wastewater and the activated sludge which enter the aeration & recirculation pump 28 into the retention chamber 1, through the control valve 41 and the discharge pipe 39.
Oxygen levels in the aeration chamber are monitored at two levels; at a low level in the high aeration zone and at an upper level at the low aeration and anoxic zones boundary, by oxygen sensors 48 & 49 respectively and an oxygen monitor 50. The oxygen levels in the aeration chamber 3 can be adjusted, to desired levels, by a manually operated air supply rate of flow control valve 53 or by the automatic air supply on/off control valve 44, by an intermittent supply of air to the aeration chamber 3.
J.K. FILE NO: 100WWT
The primary suspended solids and the activated sludge waste can be removed from the retention chamber 1 periodically or more frequently either by pumping out the sludge waste or discharging it through a control valve 15 to a designated sludge processing facility or disposal site.
The invention is not limited to the embodiment shown on Fig. 1& 2 and as outlined above, and it encompasses all the variations thereof which include installation of the aeration and recirculation pump 28 outside the aeration chamber 3, multiple aeration & recirculation pumps and air aspirator-mixers, separate aeration and recirculation pumps, open chambers without access manholes, underground and above ground chambers, separate chambers connected with pipes or channels, inlet wastewater flow meter located in a separate chamber etc.
Field of the Invention The invention relates to a process and apparatus for biological wastewater treatment as a secondary or a tertiary treatment process.
Background of the Invention Biological, activated sludge wastewater treatment process usually operates as a secondary treatment system or a tertiary treatment system for removal of Suspended Solids, Biochemical Oxygen Demand, Nitrogen and/or Phosphorous.
The treatment systems involve wastewater aeration, sludge recirculation and disposal (waste) and aerated wastewater recirculation. The aeration system can be continuous or cyclic. The aeration system usually requires air blowers and air diffusers located in aeration tanks or proprietary air aspirators are used in conjunction with a pump which pumps wastewater and air in an aeration chamber.
Simple one-pump aeration system usually operates as a secondary treatment process with a sludge recirculation or extended aeration secondary treatment process without a sludge recirculation. These processes do not provide a tertiary treatment and the secondary treatment which they provide is not well controlled and efficient. These systems usually require large tanks to provide adequate secondary treatment due to a lack of an adequate treatment process and controls in regard to sludge recirculation and disposal of excess sludge, and aeration and mixing in the aeration chamber, and recirculation of aerated wastewater.
J.K. FILE NO: 100WWT
Also, the aeration systems used are not efficient in regard to the oxygen transfer to the wastewater.
This invention is based on the wastewater aeration by means of a pump and an efficient air aspirator-mixer. The pump also recirculates and wastes the sludge produced by the biological treatment process, and recirculates the aerated wastewater to accomplish a tertiary treatment. The air aspirator-mixer is highly efficient in regard to the oxygen transfer to the wastewater.
The objectives of this invention include the following:
= To provide wastewater aeration, sludge recirculation and waste and wastewater recirculation by means of the same pump.
= To supply air to the wastewater and sludge and to mix the air and the wastewater and sludge by an efficient air aspirator-mixer.
= To provide a tertiary biological wastewater treatment process for removal of Suspended Solids, Biochemical Oxygen Demand, Nitrogen and Phosphorous and which can also be used as a secondary biological wastewater treatment for removal of Suspended Solids and Biochemical Oxygen Demand.
= To provide flexibility and control of the time and rates of the wastewater and sludge aeration, sludge recirculation and waste, and the aerated wastewater recirculation.
J.K. FILE NO: 100WWT
= To provide wastewater treatment system which can be used for small, shop fabricated treatment plants for installation above or under ground, and large, site assembled treatment plants.
= To provide wastewater treatment system which is compact and has a small foot print.
= To provide a system of low operation and maintenance requirements.
Summary of the Invention The treatment system of the present invention is a process and apparatus for biological, activated sludge treatment of municipal and industrial wastewaters.
The treatment system provides a tertiary treatment for removal of Suspended Solids, Biochemical Oxygen Demand, Nitrogen and Phosphorous. Also, the treatment system can operate as a secondary treatment for removal only of Suspended Solids and Biochemical Oxygen Demand.
The treatment system comprises primary suspended solids and excess (waste) activated sludge retention chamber, anoxic chamber, aeration chamber, clarifier chamber, wastewater aeration and recirculation, activated sludge recirculation, aeration and waste system, and instrumentation as shown on Fig. 1& 2.
A wastewater pump and an efficient air aspirator-mixer are used to provide the wastewater aeration and recirculation, and the activated sludge recirculation, aeration and waste. The wastewater pump can be a submersible pump located in the aeration chamber J.K. FILE NO: 100WWT
or a dry pit pump located beside the aeration chamber. The air aspirator-mixer is located either above or beside the aeration chamber. Single or multiple pumps and air aspirator-mixers can be used, depending on the size and capacity of the treatment system.
A wastewater effluent pump can be used instead of a non-clog wastewater pump for a better efficiency of the pumping and aeration process.
The patented J.K. air aspirator-mixer (Patent No. US 6,969,052 B2) is preferred, but other air aspirators and mixers can be used as well, if adequate air supply and the air and wastewater mixing are provided.
The primary suspended solids and the excess activated sludge retention chamber is sized either to retain the sludge for a longer period of time of several months or weeks, which may be preferred in small treatment systems, such as domestic or institutional systems, or for a much shorter period of time of several hours or days which is preferred in large treatment systems such as municipal or large industrial systems, in which case, the sludge is removed from the chamber continuously or intermittently daily for further treatment or disposal.
The aeration process can be continuous or intermittent depending on the wastewater supply pattern throughout a day or other period of time.
In the continuous aeration mode, it is preferred to control the air supply flow rate such to develop horizontal stratification zones in the aeration chamber, from the bottom to the top, of a high aeration zone, a moderate aeration zone, a light aeration zone and a J.K. FILE NO: 100WWT
mixed anoxic zone, in order to continuously provide Biochemical Oxygen Demand removal, nitrification and denitrification in the aeration chamber.
The wastewater and activated sludge are also recirculated to the anoxic chamber, located between the primary sludge holding chamber and the aeration chamber, in order to provide for phosphorous and nitrogen removal in the anoxic chamber.
In the anoxic chamber, the aerated wastewater and activated sludge are mixed with the fresh unaerated wastewater which quickly depletes the oxygen contained in the aerated wastewater, thus phosphorous and nitrogen removal processes are accomplished.
In the intermittent aeration mode, the wastewater is subjected to aeration and no aeration (anoxic) with mixing periods of approximately 1 hour to 2 hours each period.
The wastewater is recirculated to the anoxic chamber during the aeration period or both during the aeration and no-aeration periods. The intermittent aeration mode is preferred during low wastewater flow periods and no flow periods which may appear in small systems or industrial systems operated on shift basis, and low strength wastewater systems.
The use of the highly efficient air aspirator-mixer, patented by the inventor, ensures a high level of oxygen transfer to the wastewater immediately after the air is aspired into and mixed with the wastewater, and which takes place before the aerated waste water enters the aeration chamber. The oxygen transfer into the wastewater continues in the aeration chamber but it diminishes from the bottom to the top of the J.K. FILE NO: 100WWT
chamber, thus the level of aeration (oxygen transfer) is reduced from the bottom to the top and the horizontal aeration stratification zones are developed in the aeration chamber.
The other advantage is derived from the aeration stratification, that the inlet unaerated wastewater and the activated sludge return from the clarifier are mixed with the highly aerated wastewater and the mixture is further immediately re-aerated and mixed in the air aspirator-mixer and returned to the highly aerated wastewater zone.
The aeration and recirculation pump provides the aeration and recirculation of the wastewater, and the activated sludge at a flow rate of up to twelve times higher than the inlet wastewater design flow rate. The activated sludge recirculation flow rate and the aerated wastewater flow rate are several times higher than the inlet wastewater flow rate and up to 70% of the aeration/recirculation pump flow rate. The flow rates are related to the inlet wastewater quality and the required treated effluent quality.
The aerated wastewater flows into the clarifier at a flow rate of up to 100%
higher than the inlet wastewater design flow rate. The biomass developed in the aeration process settles at the bottom of the clarifier and is recirculated to the aeration chamber along with a portion of the treated wastewater which entered the clarifier.
The portion of the treated and clarified wastewater, equal to the inlet wastewater flow rate, is discharged from the clarifier to a disposal.
The activated sludge is intermittently or continuously wasted into the primary suspended solids and excess activated sludge retention chamber by intermittent or J.K. FILE NO: 100WWT
continuous discharges of the recirculated wastewater and activated sludge into the sludge retention chamber.
A portion of the wastewater and activated sludge recirculated by the aeration and recirculation pump is discharged to the upper zone in the aeration chamber, before the wastewater and activated sludge are re-aerated, to provide nutrients for the denitrification process which takes place in the upper part of the aeration chamber.
A suspended solids meter is preferred to monitor the suspended solids (mixed licquir suspended solids) density in the aeration chamber lower, high aeration zone and dissolved oxygen meters are preferred to monitor the dissolved oxygen in the aeration chamber lower, high aeration zone and the upper, low aeration/anoxic zone boundary.
A flow meter is preferred on the inlet wastewater line to monitor the inlet wastewater flow rates and volumes.
The above instrumentation is not mandatory, but it is preferred to facilitate setting up of the system operating parameters for a high efficiency performance, reliability and consistency in applications of varying inlet wastewater flow rates and quality.
Brief Descriptions of the Drawings Having thus generally described the invention, it will be referred to more specifically by reference to the accompanying drawings illustrating preferred embodiments, and in which:
J.K. FILE NO: 100WWT
Fig. 1 is a diagrammatic illustration in vertical cross-section of the treatment process and apparatus with the aeration and recirculation pump located inside the aeration chamber.
Fig. 2 is a diagrammatic illustration in horizontal cross-section of the treatment process and apparatus with the aeration and recirculation pump located inside the aeration chamber.
Detailed Description of the Invention According to the embodiment of the invention, as shown on Fig. 1& 2, the treatment system comprises the following major components: a primary suspended solids and activated sludge waste retention chamber 1, further referred to as retention chamber, an anoxic chamber 2, an aeration chamber 3, a clarifier chamber 4, access manholes 5, an inlet wastewater pipe 7, an inlet wastewater flow meter 8, an aeration and recirculation pump 28, an air aspirator-mixer 34, and an effluent wastewater pipe 47.
Inlet wastewater enters the retention chamber 1 through the inlet pipe 7, the flow meter 8 and a discharge pipe 9. The flow meter 8 is vented on the inlet and outlet sides with vent pipes 10. The discharge pipe 9 is preferably directed toward the front end of the retention chamber 1.
The inlet wastewater suspended solids and the activated waste sludge settle in the retention chamber 1 and a clarified wastewater flows toward the anoxic chamber 2, as shown by a flow direction arrow 11.
J.K. FILE NO: 100WWT
The clarified wastewater flows to an overflow trough 13 and further to the anoxic chamber 2, through a pipe 14 which connects to a wastewater and activated sludge return pipe 38, inside the anoxic chamber 2.
The clarified wastewater and recirculated wastewater and activated sludge mix together in the anoxic chamber 2 and the mixture of the wastewater and the activated sludge flows to the aeration and recirculation pump 28 through a perforated pipe 16 located in the anoxic chamber 2 and a perforated pipe 17 (single or multiple) located in the aeration chamber 3.
The aeration and recirculation pump 28 receives wastewater and activated sludge from the anoxic chamber 2, aerated wastewater from the bottom of the aeration chamber 3 and nitrified and partially denitrified wastewater from the top of the aeration chamber 3, and activated sludge from the clarifier chamber 4.
The mixture of wastewater and activated sludge is pumped into two streams;
one, an aeration stream through a pipe 33 and the air aspirator-mixer 34 where it mixes with air and the aerated mixture is discharged into the aeration chamber 3 through solid discharge pipe 35 and bottom perforated pipe 36, and the second, a recirculation stream, through a pipe 37, is not aerated and it is occasionally or continuously discharged to the retention chamber 1 through a control valve 41 and a discharge pipe 39 and to the anoxic chamber 2 through a control valve 40 and a discharge pipe 38, and to the upper part of the clarifier 3 through a control valve 55 and a discharge pipe 54.
J.K. FILE NO: 100WWT
Treated wastewater and activated sludge overflow from the aeration chamber 3 into the clarifier chamber 4 through horizontal troughs 27 and discharge pipes 26 & 25.
The discharge pipe 25 is provided with a non-return valve to prevent flow of the treated wastewater from the upper part of the clarifier chamber 4 to the aeration and recirculation pump 28.
The treated wastewater and the activated sludge separate in the clarifier chamber 4 and a clarified treated wastewater overflows to a trough 46 and further to the effluent pipe 47, and the activated sludge settles to the bottom of the clarifier chamber 4, and it is returned by the aeration and recirculation pump 28 partially to the aeration chamber 3, anoxic chamber 2 and the retention chamber 1 where the activated sludge is wasted.
The treatment processes which take place in the aeration chamber 3 comprise four horizontal zones which from the bottom to the top are high aeration, moderate aeration, low aeration and anoxic zone.
The Biochemical Oxygen Demand (BOD) removal and the nitrification of ammonia to nitrate take place in the high, moderate and low aeration zones while the denitrification process takes place in the anoxic zone.
The nitrified and partially denitrified wastewater which is returned to the anoxic chamber 2 undergoes a phosphorous removal process and further denitrification process.
A suspended solids removal is accomplished in the retention chamber 1 and in the clarifier chamber 4.
J.K. FILE NO: 100WWT
The aeration system which comprises the aeration and recirculation pump 28 and the air aspirator-mixer 34 also includes an open/close control valve 44, a rotometer 43 and an air inlet pipe 42. The rotometer 43 measures the air flow rate and the control valve 44 permits to operate the aeration chamber 3 in intermittent modes of aeration and no aeration (anoxic) while maintaining mixing of the wastewater in the aeration chamber 3 by the aeration and recirculation pump 28. This mode of operation is preferred during low flow or no flow of the inlet wastewater periods, and low strength wastewater systems.
Wastewater & activated sludge mixture flow rates into the aeration stream 33 and the recirculation stream 37, can be adjusted by manually operated valves 31 &
32.
The density of the suspended solids in the aeration chamber 3 is monitored by a suspended solids meter 52 and the desired density of the suspended solids in the aeration chamber 3 is maintained by periodical discharges of the mixture of the wastewater and the activated sludge which enter the aeration & recirculation pump 28 into the retention chamber 1, through the control valve 41 and the discharge pipe 39.
Oxygen levels in the aeration chamber are monitored at two levels; at a low level in the high aeration zone and at an upper level at the low aeration and anoxic zones boundary, by oxygen sensors 48 & 49 respectively and an oxygen monitor 50. The oxygen levels in the aeration chamber 3 can be adjusted, to desired levels, by a manually operated air supply rate of flow control valve 53 or by the automatic air supply on/off control valve 44, by an intermittent supply of air to the aeration chamber 3.
J.K. FILE NO: 100WWT
The primary suspended solids and the activated sludge waste can be removed from the retention chamber 1 periodically or more frequently either by pumping out the sludge waste or discharging it through a control valve 15 to a designated sludge processing facility or disposal site.
The invention is not limited to the embodiment shown on Fig. 1& 2 and as outlined above, and it encompasses all the variations thereof which include installation of the aeration and recirculation pump 28 outside the aeration chamber 3, multiple aeration & recirculation pumps and air aspirator-mixers, separate aeration and recirculation pumps, open chambers without access manholes, underground and above ground chambers, separate chambers connected with pipes or channels, inlet wastewater flow meter located in a separate chamber etc.
Claims (12)
1. A versatile biological wastewater treatment system for removal of Biochemical Oxygen Demand, Suspended Solids, Nitrogen and Phosphorous comprises the following major components and processes:
.cndot. Primary suspended solids and excess activated sludge retention chamber, anoxic chamber, aeration chamber, clarifier chamber, wastewater and activated sludge mixing, aeration and recirculation system.
.cndot. Inlet wastewater primary suspended solids and excess activated sludge settling, and retention process.
.cndot. Non-aerated and aerated wastewaters and activated sludge mixing and re-aeration process.
.cndot. Non-aerated and aerated wastewaters and activated sludge mixing and recirculation process.
.cndot. Treated wastewater separation of activated sludge and clear effluent process.
.cndot. Primary suspended solids and excess activated sludge retention chamber, anoxic chamber, aeration chamber, clarifier chamber, wastewater and activated sludge mixing, aeration and recirculation system.
.cndot. Inlet wastewater primary suspended solids and excess activated sludge settling, and retention process.
.cndot. Non-aerated and aerated wastewaters and activated sludge mixing and re-aeration process.
.cndot. Non-aerated and aerated wastewaters and activated sludge mixing and recirculation process.
.cndot. Treated wastewater separation of activated sludge and clear effluent process.
2. The treatment system according to Claim 1, wherein said the primary suspended solids and excess activated sludge settling and retention process is accomplished in a single chamber and the accumulated sludge is retained for a considerable period of time which is preferred in small systems or the accumulated sludge is disposed of intermittently or continuously which is preferred in medium and large systems.
3. The treatment system of Claim 1, wherein said the non-aerated and aerated wastewaters and the activated sludge mixing and re-aeration are accomplished by one aeration and recirculation pump and air aspirator-mixer system or multiple such systems, or any number of pumps and air aspirator-mixers.
4. The treatment system of Claim 3, wherein said the non-aerated and aerated wastewaters and the activated sludge are mixed and re-aerated continuously or intermittently in several optional ways; continuous mixing and re-aeration, continuous mixing and intermittent re-aeration, intermittent mixing and re-aeration, intermittent or continuous mixing and re-aeration with varying level of re-aeration (supply of air) to meet the re-aeration level requirements.
5. The treatment system of Claim 3, wherein said the mixing and re-aeration process provides horizontal stratification in the aeration chamber, from the bottom to the top, of high aerated, moderately aerated and light aerated zones and anoxic zone.
6. The treatment system of Claim 5, wherein said the horizontal aeration stratification provides for removal of Biochemical Oxygen Demand (BOD), nitrification and denitrification in the same aeration chamber.
7. The treatment system of Claim 1, wherein said the non-aerated and aerated wastewaters and the activated sludge mixing and recirculation are provided to the anoxic chamber, to the settling and retention chamber, and to the upper zone of the aeration chamber independently and intermittently or continuously to each said chamber, and simultaneously with the non-aerated and aerated wastewaters and the activated sludge mixing and re-aeration process by means of two independent streams arranged at the discharge of the aeration and recirculation pump and before the air aspirator-mixer as per Claim 3.
8. The treatment process of Claim 7, wherein said the non-aerated and aerated wastewater and activated sludge are mixed and recirculated to the upper zone of the clarifier chamber to promote the denitrification process as per Claim 6.
9. The treatment process of Claim 7, wherein said the non-aerated, and aerated wastewater and activated sludge are mixed and recirculated to the anoxic chamber to promote removal of phosphorous and to continue the denitrification process.
10. The treatment system of Claim 1, wherein said the treated wastewater separation of activated sludge and clear effluent process is accomplished in a clarifier chamber without sludge scrapers and dedicated sludge pumps to recirculate the sludge to the aeration chamber, anoxic chamber and to the sludge settling and retention chamber.
11. The treatment system of Claim 10, wherein the said activated sludge recirculation to the aeration chamber and the anoxic chamber, and the sludge settling and retention chamber is accomplished by the same aeration and recirculation pump.
12. The treatment system of Claim 10, wherein the said activated sludge settled in the clarifier chamber is withdrawn and mixed with aerated and non-aerated wastewaters and part of the mixture is re-aerated and discharged in the aeration chamber lower zone and the other part of the mixture is recirculated to the anoxic process and to the sludge settling and retention process, and the upper zone of the aeration chamber.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CA 2631906 CA2631906A1 (en) | 2008-05-15 | 2008-05-15 | Versatile biological wastewater treatment system |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CA 2631906 CA2631906A1 (en) | 2008-05-15 | 2008-05-15 | Versatile biological wastewater treatment system |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CA2631906A1 true CA2631906A1 (en) | 2009-11-15 |
Family
ID=41338172
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CA 2631906 Abandoned CA2631906A1 (en) | 2008-05-15 | 2008-05-15 | Versatile biological wastewater treatment system |
Country Status (1)
| Country | Link |
|---|---|
| CA (1) | CA2631906A1 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111453916A (en) * | 2019-01-18 | 2020-07-28 | 上海多狄环保科技有限公司 | Stem cell blood test effluent disposal system |
-
2008
- 2008-05-15 CA CA 2631906 patent/CA2631906A1/en not_active Abandoned
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111453916A (en) * | 2019-01-18 | 2020-07-28 | 上海多狄环保科技有限公司 | Stem cell blood test effluent disposal system |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US9540266B2 (en) | Moving bed media flow equalization reactor | |
| KR101192378B1 (en) | Sewage treatment apparatus equipped in underground tank | |
| SK7883Y1 (en) | Method and apparatus for waste water treatment by activation process with increased nitrogen and phosphorus removal | |
| US8641894B1 (en) | Mini metering and biological balancer control station | |
| CN101602541A (en) | Bio sewage treating process and device | |
| US8518249B2 (en) | Versatile biological wastewater treatment system | |
| CN201338965Y (en) | Biological sewage treatment device | |
| KR102171365B1 (en) | Advanced biological sewage and wastewater treatment facility of continuous flow using double tank structure | |
| RU195498U1 (en) | SEWAGE TREATMENT PLANT | |
| US8715502B1 (en) | Hoss' 4-stage biological nutrient removal (BNR) activated sludge process for removal of total phosphate and total nitrogen to a level below 1.0 mg/l without any chemical coagulation process such as alum or ferric chloride used for phosphorous removal | |
| KR20120064836A (en) | A none piping membrane bioreactor with circulation-agitater | |
| US6773596B2 (en) | Activated sludge method and device for the treatment of effluent with nitrogen and phosphorus removal | |
| CN201395543Y (en) | Aeration and sedimentation type sewage treatment system | |
| US7041219B2 (en) | Method and apparatus for enhancing wastewater treatment in lagoons | |
| CA2631906A1 (en) | Versatile biological wastewater treatment system | |
| CN211946461U (en) | Sequencing batch type sewage biological treatment device by activated sludge process | |
| PL174900B1 (en) | Method of and apparatus for biologically treating sewage | |
| CN209957477U (en) | Integrated automatic reflux shortcut nitrification and denitrification reactor | |
| JP6243804B2 (en) | Membrane separation activated sludge treatment apparatus and membrane separation activated sludge treatment method | |
| US8951412B2 (en) | Wastewater lagoon aeration treatment system | |
| CN208394884U (en) | Sewage-treatment plant | |
| CN101607774A (en) | A kind of sewage disposal device and method | |
| KR100464568B1 (en) | Device and method for Treating Waste Water | |
| CN111170435A (en) | Add medicine coagulation reaction device and be equipped with device's sewage treatment device | |
| KR100540549B1 (en) | An Apparatus for Advanced Wastewater Treatment Using Vertical Type Membrane Bio-Reactor |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| EEER | Examination request |
Effective date: 20130509 |
|
| FZDE | Dead |
Effective date: 20151030 |