US20230149848A1 - Efficient use of adsorbents for indoor air scrubbing - Google Patents

Efficient use of adsorbents for indoor air scrubbing Download PDF

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US20230149848A1
US20230149848A1 US18/092,823 US202318092823A US2023149848A1 US 20230149848 A1 US20230149848 A1 US 20230149848A1 US 202318092823 A US202318092823 A US 202318092823A US 2023149848 A1 US2023149848 A1 US 2023149848A1
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adsorbent
pollutant
regeneration
phase
adsorption
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Udi Meirav
Israel Biran
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Enverid Systems Inc
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Enverid Systems Inc
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Assigned to ENVERID SYSTEMS, INC. reassignment ENVERID SYSTEMS, INC. ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: MEIRAV, UDI, BIRAN, ISRAEL
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/02Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
    • B01D53/04Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with stationary adsorbents
    • B01D53/0454Controlling adsorption
    • BPERFORMING OPERATIONS; TRANSPORTING
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    • B01D53/02Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
    • B01D53/04Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with stationary adsorbents
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    • B01D53/02Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
    • B01D53/04Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with stationary adsorbents
    • B01D53/0407Constructional details of adsorbing systems
    • B01D53/0446Means for feeding or distributing gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
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    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/346Controlling the process
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
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    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/81Solid phase processes
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    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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    • BPERFORMING OPERATIONS; TRANSPORTING
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    • BPERFORMING OPERATIONS; TRANSPORTING
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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    • B01D2259/40Further details for adsorption processes and devices
    • B01D2259/414Further details for adsorption processes and devices using different types of adsorbents
    • B01D2259/4141Further details for adsorption processes and devices using different types of adsorbents within a single bed
    • B01D2259/4145Further details for adsorption processes and devices using different types of adsorbents within a single bed arranged in series
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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    • B01D2259/45Gas separation or purification devices adapted for specific applications
    • B01D2259/4508Gas separation or purification devices adapted for specific applications for cleaning air in buildings
    • 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
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/10Capture or disposal of greenhouse gases of nitrous oxide (N2O)
    • 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
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/40Capture or disposal of greenhouse gases of CO2

Definitions

  • Embodiments of the present disclosure generally relate to air management systems and particularly to air management systems including adsorbent based air treatment systems.
  • HVAC Heating, Ventilation and Air-Conditioning
  • the HVAC system primary role is to maintain comfortable temperature and humidity, as well as good indoor air quality.
  • the circulating air should be refreshed, either by continually replacing it with fresh air from outside the enclosed environments, or by treating it for removal of unwanted contaminants that tend to form or buildup in the enclosed environments.
  • the contaminants may also be referred to as pollutants, or substances.
  • pollutants may include carbon dioxide (CO 2 ) as well as volatile organic compounds (VOCs), inorganic gases like sulfur oxides, nitrous oxides, carbon monoxide, radon and others.
  • Particles and microorganisms also represent non-gaseous pollutants that affect indoor air quality and should be filtered or removed. Since replacement of indoor air may not provide a satisfactory solution - whether due to the thermal load it imposes on the HVAC system, or due the poor air quality of the outside air, or lack of access to outside fresh air, indoor air may be treated by means of adsorbents to remove gas pollutants.
  • Regeneration may be performed by streaming a purge gas (which may also be referred to as a regeneration gas) over and/or through the adsorbent.
  • a purge gas which may also be referred to as a regeneration gas
  • the adsorbent may be flushed with air or some other gas that has a higher temperature and/or lower partial pressure of pollutants, or by heating the adsorbent itself, whereby the pollutant molecules are carried off the adsorbent surface.
  • adsorbents are often used in an adsorption- desorption “swing cycle” where in the adsorption, or cleaning, part of the cycle, they capture certain species of gases, and continue to do so until the adsorbent reaches saturation. During desorption, or a regeneration cycle, they release the gases which were adsorbed until they recover their original capacity and adsorption efficiency, at which point a new cycle can begin.
  • the swing cycle can be at least one of, for example, a temperature-swing cycle, pressure-swing cycle, or a concentration-swing adsorption cycle. In some cases both temperature and concentration, or temperature and pressure, may be changed during regeneration.
  • regenerable adsorbents for removing carbon dioxide (CO 2 ) and VOCs in indoor air, relying on a swing cycle is an important alternative to air replacement, especially when the outside conditions make air replacement energetically costly, environmentally undesirable or otherwise impractical.
  • regeneration economics and performance are critical, as regeneration represents downtime for the air treatment function and energy must be consumed to flow the purge gas and release the pollutants. Finding the optimal economic and functional performance is further complicated by varying conditions of pollutant species and concentration levels, as well as temperature and flow rates.
  • systems and methods are described for removal of CO 2 and other pollutants from indoor air using adsorbents and a temperature-or concentration-swing adsorption cycle.
  • reversing the direction of flow during regeneration can provide advantages when one type of pollutant is present and when more than one type of pollutant is present.
  • a method for reducing the level of at least one pollutant contained in indoor air from a human-occupied, enclosed environment may comprise providing an air treatment assembly including at least one type of adsorbent, the adsorbent may be configured for capturing at least one pollutant entrained in an indoor air flow from the enclosed environment and regenerating upon exposure to a regenerating gas flow; streaming the indoor air flow over and/or through the adsorbent in a first direction such that the adsorbent captures at least some of the pollutant from the indoor air flow, where after being flowed over and/or through the adsorbent, the air flow comprises a scrubbed air flow; and streaming the regeneration gas flow over and/or through the adsorbent in a second direction opposite to the first direction, such that the regeneration gas flow regenerates at least some of the adsorbent and purges at least some of the pollutant from the adsorbent.
  • the air treatment assembly comprises at least two adsorbents such that the streaming indoor air flows through a first adsorbent and subsequently through a second adsorbent, and that as a result of the reversal of the flow direction during regeneration, substances purged from the first adsorbent do not flow across the second adsorbent.
  • pollutants may be released from the one adsorbent during regeneration and may accumulate in the air treatment assembly or air conduits attached to it, and as a result of the reversal of the flow direction during regeneration, the released pollutants are substantially prevented from accumulating downstream from the adsorbent and accumulate substantially in sections of the air treatment assembly that are upstream from the adsorbent
  • the air treatment assembly may comprise an inlet for indoor air flowing through the adsorbent and upstream the adsorbent being in greater proximity to the inlet than downstream the adsorbent.
  • the pollutant and/or first gas may be selected from the group consisting of: carbon dioxide, volatile organic compounds, sulfur oxides, radon, nitrous oxides and carbon monoxide.
  • the adsorbent may comprise at least one of an amine supported by a solid, activated carbon, clay, carbon fibers, silica, alumina, zeolites, molecular sieves, titanium oxide, polymer, porous polymers, polymer fibers and metal organic framework.
  • the supporting solid may be at least one of silica, carbon, clay or metal oxide.
  • the adsorbent may comprise granular solids or pelleted shaped solids.
  • a computer implemented method for reducing the level of at least one pollutant contained in indoor air from an enclosed, human-occupied environment may comprise streaming an indoor air flow over and/or through an adsorbent provided within an air treatment assembly in a first direction, the indoor air flow containing at least one pollutant from inside the enclosed environment, such that the adsorbent captures at least some of the pollutant from the indoor air, where after being flowed over and/or through the adsorbent, the air flow comprises a scrubbed air flow, determining a level of an adsorption efficiency, where the adsorption efficiency at any point in time during the one cycle has a value of 1 - C in /C out , where C in is the concentration of the pollutant in the incoming air flow and C out is the concentration of the pollutant in an outgoing air flow, and where an initial adsorption efficiency value is the adsorption efficiency value at the beginning of the adsorption phase, where the a
  • a system for reducing the level of at least one pollutant contained in indoor air from an enclosed, human-occupied environment may comprise an air treatment assembly including an adsorbent, the adsorbent may be configured for capturing at least one pollutant entrained in an indoor air flow and regenerating upon exposure to a regenerating gas flow; and streaming means for streaming the indoor air flow over and/or through the adsorbent in a first direction, such that the adsorbent captures at least some of the at least one pollutant from the indoor air flow, and streaming the regeneration air flow over and/or through the adsorbent in a second direction opposite to the first direction, such that the regeneration gas flow regenerates at least some of the adsorbent and purges at least some of the pollutant from the adsorbent.
  • a system for reducing the level of at least one pollutant contained in indoor air from an enclosed, human-occupied environment may comprise an air treatment assembly including an adsorbent, the adsorbent configured for capturing at least one pollutant entrained in an indoor air flow and regenerating upon exposure to a regenerating gas flow, streaming means for streaming the indoor air flow over and/or through the adsorbent in a first direction, and/or for streaming the regeneration gas flow over and/or through the adsorbent in a second direction opposite to the first direction; at least one processor; a non-transitory machine-readable medium storing instructions that, when executed by the processor, perform the method, which may comprise: streaming the indoor air over and/or through the adsorbent in the first direction such that the adsorbent captures at least some of the pollutant from the indoor air; and determining a level of an adsorption efficiency, where the adsorption efficiency at any point in time during the one
  • a method for controlling a scrubber containing an adsorbent configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the at least one pollutant and/or first gas being adsorbed onto the adsorbent, and regenerating at least some of the adsorbent and thereby purging at least some of the at least one pollutant and/or first gas from the adsorbent via a regeneration gas flow.
  • the method may comprise flowing a stream of gases through the scrubber, the scrubber comprising the adsorbent, adsorbing at least some of the one pollutant and/or first gas from the stream of gases onto the adsorbent during an adsorption phase over a first time period, purging a portion of the at least one pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and cycling between the adsorption phase and the regeneration phase.
  • the method may also include limiting at least one of: the duration of the first time period to a period of time which is less than the time required to have the adsorbent adsorb as much of the pollutant/gas as the adsorbent can adsorb complete adsorption phase, and the duration of the second time period to a period of time which is less than the time required to completely regenerate the adsorbent.
  • a method for reducing the level of at least one pollutant contained in indoor air from an enclosed, human-occupied environment may comprise providing an air treatment assembly including an adsorbent, the adsorbent configured for capturing at least one pollutant entrained in an indoor air flow from the enclosed environment and regenerating upon exposure to a regenerating gas flow streaming the indoor air flow over and/or through the adsorbent in a first direction such that the adsorbent captures at least some of the at least one pollutant from the indoor air flow, where the streaming of the indoor air flow over and/or through the adsorbent comprises an adsorption phase; and streaming the regeneration gas flow over and/or through the adsorbent in a second direction opposite to the first direction, such that the regeneration air flow regenerates at least some of the adsorbent and purges at least some of the at least one pollutant from the adsorbent, where the streaming of the regeneration gas flow over and/or through the
  • the method may further include determining a level of an adsorption efficiency, where the adsorption efficiency at any point in time during the one cycle has a value of 1 - C in /C out , where C in is the concentration of the pollutant in the incoming air flow and C out is the concentration of the pollutant in an outgoing air flow, and where an initial adsorption efficiency value is the adsorption efficiency value at the beginning of the adsorption phase, where the adsorption efficiency value is less than the initial adsorption efficiency value, streaming of the regeneration gas flow over and/or through the adsorbent is performed.
  • the adsorption efficiency value is at least about 20% less than the initial adsorption efficiency value. In accordance with some embodiments the adsorption efficiency value is at least about 30% less than the initial adsorption efficiency value. In accordance with some embodiments the adsorption efficiency value is at least about 50% less than the initial adsorption efficiency value. In accordance with some embodiments the adsorption efficiency value is at least about 80% less than the initial adsorption efficiency value.
  • a key for optimal system economics is to terminate the regeneration phase and the adsorption phase before they are complete, as the rates of adsorption and desorption decline.
  • a detailed analysis shows how to identify and set the optimal points at which to switch over from regeneration to adsorption and vice versa.
  • the scrubber may be configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the pollutant and/or first gas being adsorbed onto the adsorbent, and regenerating at least some of the adsorbent and thereby purging at least some of the pollutant and/or first gas from the adsorbent via a regeneration gas flow.
  • the method may include flowing a stream of gases through the scrubber, the scrubber comprising the adsorbent; adsorbing at least some of the pollutant and/or first gas from the stream of gases onto the adsorbent during an adsorption phase over a first time period; purging a portion of the pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and cycling between the adsorption phase and the regeneration phase.
  • One cycle may comprise at least an adsorption phase followed by a regeneration phase, one cycle period may comprise the total time elapsed during one cycle.
  • the pollutant and/or first gas purged from the adsorbent may be carried away by the regeneration gas flow.
  • a complete regeneration phase may comprise a time period for removing substantially all of the pollutant and/or first gas from the adsorbent during the regeneration phase
  • a complete adsorption phase may comprise a time period for substantially saturating all the adsorbent during the adsorption.
  • the method may include limiting at least one of: the duration of the first time period to a period of time which is less than the complete adsorption phase, and/or the duration of the second time period to a period of time which is less than the complete regeneration phase.
  • the first time period may comprise about 95% of a complete adsorption phase. In accordance with some embodiments, the first time period is about 90% of a complete adsorption phase. In accordance with some embodiments, the first time period is about 80% of a complete adsorption phase. In accordance with some embodiments, the first time period is about 50% of a complete adsorption phase. In accordance with some embodiments, the first time period is about 20% of a complete adsorption phase. In accordance with some embodiments, the first time period comprises about 20% to about 95% of a complete adsorption phase.
  • the second time period comprises about 95% of a complete regeneration phase. In accordance with some embodiments, the second time period is about 90% of a complete regeneration phase. In accordance with some embodiments, the second time period is about 80% of a complete regeneration phase. In accordance with some embodiments, the second time period is about 50% of a complete regeneration phase. In accordance with some embodiments, the second time period is about 20% of a complete regeneration phase. In accordance with some embodiments, the second time period comprises about 20% to about 95% of a complete regeneration phase.
  • the regeneration phase may be terminated upon a regeneration rate R(t r ) of the adsorbent being between about equal to and a predetermined amount less than a productivity p of the complete regeneration phase, where productivity
  • C equals an amount of the pollutant and/or first gas adsorbed by the adsorbent from the stream of gases during one cycle and T is the duration of one cycle period.
  • the regeneration phase is terminated upon a regeneration rate R(t r ) being between about equal to and about twice a productivity p of the complete regeneration phase, where productivity
  • C equals an amount of the pollutant and/or first gas adsorbed by the adsorbent from the stream of gases during one cycle and T is the duration of one cycle period.
  • the pollutant and/or first gas may be selected from the group consisting of: carbon dioxide, volatile organic compounds, sulfur oxides, radon, nitrous oxides and carbon monoxide.
  • the adsorbent may comprise at least one of: an amine supported by a solid, activated carbon, clay, carbon fibers, silica, alumina, zeolites, molecular sieves, titanium oxide, polymer, porous polymers, polymer fibers and metal organic frameworks.
  • the supporting solid may be at least one of silica, carbon, clay or metal oxide.
  • the adsorbent may comprise granular solids or pelleted shaped solids.
  • the stream of gases may comprise air from an enclosed environment, outdoor air, flue gases, or nitrogen with elevated levels of carbon dioxide or organic contaminants, relative to substantially unpolluted air.
  • the one cycle may further comprise at least one of: (i) a first switchover phase prior to the regeneration phase, and (ii) a second switchover phase following the regeneration phase.
  • the second switchover phase may comprise a period of time to bring the adsorbent to a temperature to adsorb pollutant and/or first gas during the adsorption phase.
  • the first switchover phase may comprise a period of time to bring the adsorbent to a temperature to release the at least one pollutant and/or first gas from the adsorbent during the regeneration phase.
  • the method may further include determining a level of an adsorption efficiency, where the adsorption efficiency at any point in time during the one cycle has a value of 1 - C in /C out , where C in is the concentration of the pollutant in the incoming air flow and C out is the concentration of the pollutant in an outgoing air flow, and where an initial adsorption efficiency value is the adsorption efficiency value at the beginning of the adsorption phase.
  • the adsorption efficiency value is less than the initial adsorption efficiency value, streaming of the regeneration gas flow over and/or through the adsorbent is performed.
  • a system for controlling a scrubber may comprise a scrubber containing an adsorbent, the scrubber may be configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the at least one pollutant and/or first gas being adsorbed onto the adsorbent, and purging the at least one pollutant and/or first gas from the adsorbent via a regeneration gas flow; means for flowing the stream of gases through the scrubber and over and/or through the adsorbent, where the adsorbent adsorbs at least one pollutant and/or first gas from the stream of gases during an adsorption phase over a first time period; means for flowing the regeneration gas flow over the adsorbent for purging a portion of the pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and means for cycling between the adsorption phase and the
  • One cycle may comprise one adsorption phase followed by one regeneration phase.
  • One cycle period may comprise the total time elapsed during one cycle.
  • the pollutant and/or first gas purged from the adsorbent may be carried away by the regeneration gas flow.
  • a complete regeneration phase may comprise a time period for removing substantially all of the pollutant and/or first gas from the adsorbent during the regeneration phase.
  • a complete adsorption phase comprises a time period for substantially saturating all the adsorbent during the adsorption.
  • the duration of at least one of the following may be limited: the duration of the first time period to a period of time which is less than the complete adsorption phase, and the duration of the second time period to a period of time which is less than the complete regeneration phase.
  • the means for cycling may comprise a processor and a non-transitory machine-readable medium storing instructions (for example), having computer instructions/code operating thereon for controlling cycling between the adsorption and regeneration phases.
  • a computer implemented method for controlling a scrubber containing an adsorbent the scrubber may be configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the at least one pollutant and/or first gas being adsorbed onto the adsorbent, and purging the at least one pollutant and/or first gas from the adsorbent via a purging gas flow, the method comprising: flowing a stream of gases through the scrubber, the scrubber including or comprising an adsorbent; adsorbing at least one pollutant and/or first gas from the stream of gases onto the adsorbent during an adsorption phase over a first time period, purging a portion of the at least one pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and cycling between the adsorption phase and the regeneration phase.
  • One cycle may comprise one adsorption phase followed by one regeneration phase.
  • One cycle period may comprise the total time elapsed during one cycle.
  • At least one pollutant and/or first gas purged from the adsorbent may be carried away by the regeneration gas flow.
  • a complete regeneration phase comprises a time period for removing substantially all of the pollutant and/or first gas from the adsorbent during the regeneration phase.
  • a complete adsorption phase may comprise a time period for substantially saturating all the adsorbent during the adsorption.
  • the method may include limiting at least one of: the duration of the first time period to a period of time which is less than the complete adsorption phase, and the duration of the second time period to a period of time which is less than the complete regeneration phase, where at least one of the above is performed by at least one processor.
  • the scrubber may be configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the pollutant and/or first gas being adsorbed onto the adsorbent, and purging the pollutant and/or first gas from the adsorbent via a regeneration gas flow.
  • the system may comprise at least one processor and a non-transitory machine-readable medium storing instructions that, when executed by the at least one processor, perform the method which may comprise: flowing a stream of gases over and/or through the adsorbent, where the adsorbent adsorbs at least some of the pollutant and/or first gas from the stream of gases during an adsorption phase over a first time period; purging a portion of the pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and cycling between the adsorption phase and the regeneration phase.
  • One cycle may comprise one adsorption phase followed by one regeneration phase.
  • One cycle period may comprise the total time elapsed during one cycle.
  • At least one pollutant and/or first gas purged from the adsorbent may be carried away by the regeneration gas flow.
  • a complete regeneration phase comprises a time period for removing substantially all of the pollutant and/or first gas from the adsorbent during the regeneration phase.
  • a complete adsorption phase may comprise a time period for substantially saturating all the adsorbent during the adsorption.
  • the method may include limiting at least one of: the duration of the first time period to a period of time which is less than the complete adsorption phase, and the duration of the second time period to a period of time which is less than the complete regeneration phase.
  • FIGS. 1 A- 1 C are each a schematic illustration of an air management system according to some embodiments of the present disclosure
  • FIGS. 2 A and 2 B are each a schematic illustration of an air management system according to some embodiments of the present disclosure
  • FIG. 3 is a schematic illustration of an air treatment assembly according to some embodiments of the present disclosure.
  • FIG. 4 is a graph showing an adsorption-regeneration cycle according to some embodiments of the present disclosure.
  • adsorbents such as solid adsorbents, are used to scrub unwanted pollutants including gases and vapors, from indoor air, namely pollutants entrained in an indoor air flow from the enclosed environment.
  • Adsorbents selective to CO 2 include, but are not limited to, various types of amines and solid-supported amines, as well as clays, molecular sieves, zeolites, various forms of silica and alumina, various forms of carbon, activated carbon, carbon fibers, titanium oxide, porous polymers, polymer fibers and metal organic frameworks.
  • Adsorbents selective to VOCs may include molecular sieves, activated carbon, zeolites, carbon fibers and carbon particles, for example. In some embodiments more than one type of adsorbent is used.
  • first layer or bed of an adsorbent for capturing CO 2 there may be a first layer or bed of an adsorbent for capturing CO 2
  • second layer of an adsorbent for capturing VOCs positioned downstream from the first layer, relative to the direction of the air flow of incoming indoor air.
  • the first layer may comprise solid supported amines for capturing CO 2
  • the second layer may comprise carbon adsorbents for capturing VOCs.
  • FIGS. 1 A- 1 C are each a schematic illustration of an air management system 100 including a scrubber, which may be referred to as an air treatment assembly 102 .
  • the air management system 100 may include an air circulation system, such as a central HVAC system 108 provided to manage and circulate indoor air within an enclosed environment 110 .
  • the enclosed environment 110 may comprise an office building, a commercial building, a bank, a residential building, a house, a school, a factory, a hospital, a store, a mall, an indoor entertainment venue, a storage facility, a laboratory, a vehicle, an aircraft, a ship, a bus, a theatre, a partially and/or fully enclosed arena, an education facility, a library and/or other partially and/or fully enclosed structure and/or facility which can be at times occupied by equipment, materials, live occupants (e.g., humans, animals, synthetic organisms, etc.) and/or any combination thereof.
  • an office building a commercial building, a bank, a residential building, a house, a school, a factory, a hospital, a store, a mall, an indoor entertainment venue, a storage facility, a laboratory, a vehicle, an aircraft, a ship, a bus, a theatre, a partially and/or fully enclosed arena, an education facility, a library and/or other partially and/or
  • the HVAC system 108 shown in FIGS. 1 A- 1 C may comprise an air handling unit 114 in fluid communication with the enclosed environment 110 .
  • the air handling unit 114 may provide air circulation to various parts of the enclosed environment 110 by means of ducts 116 or conduits, as shown in FIGS. 1 A- 1 C .
  • the air handling unit 114 may include any suitable configuration for conditioning the temperature and humidity of the air flowing through it.
  • Conditioned air exiting the air handling unit 114 may be provided to the enclosed environment 110 as supply air 118 .
  • Return air 120 which is indoor air 120 from the enclosed environment 110 , may exit the enclosed environment 110 via ducts 122 or a plenum or any other suitable means.
  • a portion of the return air 120 may be exhausted as exhaust air 124 , directly or via ducts 126 . Outside, fresh air 130 may be introduced into the air handling unit 114 via ducts 132 .
  • the air treatment assembly 102 may be placed in any suitable location within the enclosed environment relative to the air management system 100 and is configured to receive at least a portion of the indoor air. In some embodiments, as shown in FIG. 1 A , the air treatment assembly 102 is placed in parallel to the air handling unit 114 . A portion of the return air 120 may flow to the air treatment assembly 102 and thereafter to the air handling unit 114 and the remaining portion may flow directly to the air handling unit 114 and/or may be exhausted as exhaust air 124 , via ducts 126 .
  • the air treatment assembly 102 is placed in series with the air handling unit 114 , either upstream relative to the air handling unit 114 or downstream thereof. A portion of the return air 120 may flow to the air treatment assembly 102 and thereafter to the air handling unit 114 and a portion may be exhausted as exhaust air 124 , via ducts 126 .
  • the air treatment assembly 102 is not in direct fluid communication with the air handling unit 114 , and may be placed within the enclosed environment 110 . A portion of circulating indoor air 120 may flow into the air treatment assembly 102 and thereout, back into the enclosed environment 110 .
  • FIGS. 2 A and 2 B are each a schematic illustration of an air management system 200 comprising the air treatment assembly 102 .
  • the air management system 200 may include a distributed air circulation system 208 comprising one or more fan-coil units 210 provided to manage and circulate indoor air within the enclosed environment 110 .
  • the enclosed environment 110 may comprise a plurality of rooms 220 .
  • a fan-coil unit 210 may be placed in one or more of the rooms 220 .
  • An air treatment assembly 102 may be placed in one or more of the rooms 220 .
  • At least a portion of return air 120 comprising indoor air from the room 220 , may flow into the air treatment assembly 102 and a separate stream of air may flow into the fan-coil unit 210 and/or may be exhausted out of the room 220 .
  • the air treatment assembly 102 may be placed at any suitable location. In some embodiments, as shown in FIG. 2 A , scrubbed air flowing out of the air treatment assembly 102 may flow directly to the fan-coil unit 210 via a duct 222 .
  • the air treatment assembly 102 may not be in direct fluid communication with the fan-coil unit 210 . At least a portion of indoor air 120 may flow into the air treatment assembly 102 and a portion may flow into the fan-coil unit 210 .
  • the air treatment assembly 102 may be provided to reduce the concentration of unwanted substances or pollutants present in the air introduced therein.
  • the air treatment assembly 102 may comprise one or more adsorbent beds or layers for one or more types of pollutants.
  • a first adsorbent 230 may be provided for capturing gas pollutants, such as CO 2 and a second adsorbent 234 may be provided for capturing other gas pollutants, such as VOCs.
  • Examples of air treatment assemblies are disclosed in applicant’s U.S. Pat. No. 8157892, which is incorporated herein by reference in its entirety.
  • the CO 2 adsorbent 230 may comprise a solid supported amine, such as disclosed in applicant’s PCT application PCT/US12/38343, which is incorporated herein by reference in its entirety.
  • the first adsorbent 230 may be formed of an adsorbent bed comprising adsorbent particles 236 .
  • the adsorbent particles 236 may comprise solid supported amines or any other adsorbent material, in any suitable form, such as granular solids or pelleted shaped solids, for example.
  • the second adsorbent 234 may be formed of a layer 238 comprising a carbon cloth or any other suitable material.
  • the air treatment assembly 102 may operate in a cycle comprising an adsorption phase and a regeneration phase.
  • the pollutants such as the CO 2 or VOCs
  • the adsorbents which as described above, may comprise one or more adsorbents, such as adsorbents 230 and 234 .
  • the adsorbent may be regenerated during the regeneration phase by urging the release of the pollutants therefrom.
  • the regeneration may be performed in any suitable manner.
  • regeneration may be performed by exposing, (e.g. by flushing) the adsorbent to a purge gas for purging and releasing at least a portion of the pollutants therefrom.
  • the purge gas may comprise outdoor air 240 .
  • the outdoor air 240 may be heated prior to entering the air treatment assembly 102 by any suitable method, such as will be further described.
  • FIGS. 1 A- 3 Incoming contaminated indoor air 120 from the enclosed environment 110 is shown in FIGS. 1 A- 3 as flowing in a first direction into the air treatment assembly 102 through an aperture or a first inlet 244 , which may be controlled by an inlet damper 248 or any other suitable means. Scrubbed air may exit the air treatment assembly 102 via an oppositely facing aperture or second outlet 250 , which may be controlled by an outlet damper 254 or any other suitable means.
  • the incoming side is referred to as upstream and the outgoing side as downstream.
  • the outdoor air 240 may flow into the air treatment assembly 102 via an inlet 260 , which may be controlled by an inlet damper 264 .
  • the outside air 240 may flow out of the air treatment assembly 102 via an outlet 268 , which may be controlled by an outlet damper 270 .
  • the inlet damper 264 and outlet damper 270 may be open during the regeneration phase while the inlet damper 248 and outlet damper 254 are generally closed.
  • the inlet damper 264 and outlet damper 270 may be closed while the inlet damper 248 and outlet damper 250 are generally open.
  • the outdoor air 240 may flow into a heating subassembly 280 for heating the outdoor air 240 therein before entering the air treatment assembly 102 .
  • Heating the outdoor air 240 may be performed in any suitable manner, such as by an electrical heating coil placed within the heating subassembly 280 . Additional methods for heating the outdoor air 240 include: water coils using hot water provided from a separate source; direct or indirect solar heat; a furnace using gas or other fuel; a heat pump; or any other suitable source of heat.
  • the outdoor air 240 may be heated from the ambient temperature to any suitable temperature, typically within a range of approximately 30-120° C. Alternatively, the outdoor air 240 may be heated to a temperature less than 80° C. Alternatively, the outdoor air 240 may be heated to a temperature less than 50° C. Alternatively, the outdoor air 240 may enter the air treatment assembly 102 at the ambient temperature without prior heating thereof.
  • the heating subassembly 280 may be placed in any suitable location.
  • the heating subassembly 280 may be placed in proximity to the air treatment assembly 102 or may be located at a certain distance whereby warm, outdoor air 240 may be delivered from the heating subassembly 280 to the air treatment assembly 102 via a conduit (not shown).
  • the outdoor air 240 during the regeneration phase may flow in a second direction, which is the opposite direction of the indoor air flow during the adsorption phase (i.e. the first direction).
  • the air treatment assembly 102 may be configured with an appropriate fan 290 or fans that either pushes the outside air 240 into the air treatment assembly 102 near the inlet 260 or pulls the outside air 240 thereout at outlet 268 , as shown in FIGS. 1 A- 3 .
  • the fan 290 can be part of the air treatment assembly 102 or can be incorporated into the air heating subassembly 280 or any other suitable location within the air management system 100 of FIGS. 1 A- 1 C or air management system 200 of FIGS. 2 A and 2 B .
  • the air treatment assembly 102 may comprise additional fans, such as fan 292 , for pushing or pulling the return air 120 through the air treatment assembly 102 .
  • the direction of air flow in regeneration is in the same direction of the return air flow.
  • the reverse air flow during the regeneration phase offers certain advantages which are best understood in relation to FIG. 3 and inserts thereof.
  • pollutant laden air first encounters an upstream section or surface 300 of the adsorbent bed and the air is gradually depleted of CO 2 or other pollutants as it advanced through the bed, away from surface 300 .
  • the adsorbent material near this surface 300 receives the most contaminated air and as a result, there is typically a higher load of captured pollutants 304 in the upstream side of the adsorbent bed, than in an oppositely facing surface 308 in the downstream side of the adsorbent bed.
  • the pollutants carried from the upstream side are forced to flow through the entire bed on their way out, and through subsequent adsorbent layers (such as layer 238 ) if there are such. This may increase the likelihood that some of these purged pollutants will be recaptured. If the flow is reversed, the highest concentration of pollutants is removed backwards and away from the upstream section without passing through the bed. A similar dynamic may apply also to captured dust particles 310 .
  • the considerations is also significant when a dual adsorbent system is deployed, such as with the second adsorbent 234 , e.g. the VOC adsorbent layer 238 , downstream from the first adsorbent 230 , such as the CO 2 adsorbent.
  • the CO 2 adsorbent may release VOCs and particles or vapors 314 during regeneration.
  • a solid supported amine based CO 2 adsorbent may release some amine vapors 314 during high temperature regeneration.
  • vapors 314 are preferably exhausted directly and not forced to flow through the VOC adsorbent where they may be captured, thus loading and contaminating the VOC adsorbent 234 instead of allowing it to be purged and regenerated.
  • clean air passes though the VOC adsorbent 234 first and then through the CO2 adsorbent 230 , so that any volatilized amines are carried away from the VOC adsorbent 234 rather than through it.
  • granular adsorbents 236 may release their own dust particles 310 and it is preferable to exhaust them without passing them through the air treatment assembly 102 downstream dust filter 320 or a fiber cloth, such as layer 238 , where dust particles 310 can buildup and impede air flow.
  • the reverse air flow during the regeneration phase may be significant in any air treatment assembly including or comprising a single or plurality of adsorbents configured to adsorb any pollutants from incoming air.
  • pollutants may be released from the adsorbent during regeneration and may accumulate in the air treatment assembly 102 or air conduits attached to it or sections of the air treatment assembly 102 .
  • the released pollutants may be substantially prevented from accumulating downstream from the adsorbent and accumulate substantially in sections of the air treatment assembly that are upstream from the adsorbent.
  • Upstream the adsorbent may also be defined as being in greater proximity to the inlet 244 than downstream the adsorbent.
  • any other suitable means besides dampers such as valves, fans or shutters, may be used to control the volume of air entering and/or exiting the air treatment assembly 102 or flowing the incoming air (or stream of gases) through the air treatment assembly 102 .
  • blowers or any other suitable means for urging flow of air may be used in place of or in addition to the fans of the air treatment assembly 102 .
  • any suitable streaming means may be provided, such as dampers, fans, (such as shown in FIG. 3 ), valves, and/or shutters and ducts inlets and outlets (such as shown in FIGS. 1 A- 3 ) and/or conduits.
  • the streaming means may be used for streaming the indoor air flow over and/or through the adsorbent in the first direction, such that the adsorbent captures at least the pollutant or first gas from the indoor air flow.
  • the streaming means may further be used for streaming the regeneration air flow over and/or through the adsorbent in the second direction opposite to the first direction, such that the regeneration gas flow regenerates at least some of the adsorbent and purges at least some of the pollutant from the adsorbent.
  • the air management system 100 of FIGS. 1 A- 1 C or air management system 200 of FIGS. 2 A and 2 B may include fans, and dampers or any other suitable means for circulating air therein.
  • the adsorbent gradually becomes saturated with CO 2 (or other pollutants) and its ability to adsorb begins to degrade, eventually stopping adsorption entirely.
  • the transition can be gradual or fairly sharp, depending on a number of parameters including the flow rate, temperature, thickness of adsorbent bed, and of course the chemistry and structural properties of the adsorbent.
  • the adsorbent is purged.
  • the amount of adsorbed gas that is released is initially high and then gradually declines as the adsorbent is depleted from the captured gas.
  • the time spent regenerating the adsorbent is time when the adsorbent is “off line” and not being utilized. This time spent regenerating may be kept as short as possible.
  • an adsorption-regeneration cycle that is incomplete, limited or interrupted by design.
  • the phases are switched from adsorption to regeneration before the adsorbent is saturated, and the regeneration process may be stopped well before all the pollutants are released. This is done in order to achieve the best economics for indoor air scrubbing.
  • the air treatment assembly 102 or scrubber may be configured to cycle between scrubbing at least one pollutant and/or gas from the stream of gases with the pollutant, and regenerating at least some of the adsorbent.
  • the adsorption-regeneration cycle may comprise an adsorption phase which may be followed by a regeneration phase.
  • a complete adsorption phase may comprise a first time period for substantially saturating the adsorbent during the adsorption phase under the adsorption flow and temperature conditions being used.
  • a complete regeneration phase may comprise a second time period for removing substantially all of the removable pollutants and/or first gas from the adsorbent during the regeneration phase, under the purge flow and temperature conditions being used.
  • the duration of the second time period may be limited to a period of time which is less than the complete regeneration phase. Additionally or alternatively, the duration of the first time period may be limited to a period of time which is less than the complete adsorption phase.
  • the adsorption-regeneration cycle may comprise an adsorption phase followed by an optional first switchover time period, which may be followed by a regeneration phase.
  • the regeneration phase may be followed by an optional second switchover time period.
  • the adsorbent may be heated or may be maintained at the same temperature. In some embodiments, during the second switchover time period the adsorbent may be cooled down. The cool down may be facilitated by flowing unheated air through the sorbent during this time.
  • the first switchover time period may comprises a period of time to bring the adsorbent to a temperature to release the pollutant from the adsorbent during the regeneration phase.
  • the second switchover time period may comprise a period of time to bring the adsorbent to a temperature to adsorb the pollutant during the adsorption phase.
  • the first time period may comprise about 95% of a complete adsorption phase. In some embodiments, the first time period may comprise about 90% of a complete adsorption phase. In some embodiments, the first time period may comprise about 80% of a complete adsorption phase. In some embodiments, the first time period may comprise about 50% of a complete adsorption phase. In some embodiments, the first time period may comprise about 20% of a complete adsorption phase. In some embodiments, the first time period may comprise about 20%-95% of a complete adsorption phase.
  • the second time period may comprise about 95% of a complete regeneration phase. In some embodiments, the second time period may comprise about 90% of a complete regeneration phase. In some embodiments, the second time period may comprise about 80% of a complete regeneration phase. In some embodiments, the second time period may comprise about 50% of a complete regeneration phase. In some embodiments, the second time period may comprise about 20% of a complete regeneration phase. In some embodiments, the second time period may comprise about 20%-95% of a complete regeneration phase.
  • Determining the duration of the limited period of time for the regeneration phase and/or the adsorption phase may be performed in any suitable manner, such as empirically via experimentation, for example.
  • determining the duration of the limited period may be performed by a computer including a processor and a non-transitory machine-readable medium (for example).
  • controlling cycling between the adsorption and regeneration phases may be performed by a computer including a processor and a non-transitory machine-readable medium, storing instructions having computer instructions operating thereon (for example).
  • optimizing the cycle length and regeneration time may be performed by a system for controlling the air treatment assembly 102 (which may be referred to as the scrubber).
  • the air treatment assembly 102 containing the adsorbent may be configured to cycle between scrubbing the pollutant and/or gas from the stream of gases in the incoming air and/or gas being adsorbed onto the adsorbent, and purging the pollutant and/or first gas from the adsorbent, via the regeneration gas flow.
  • the air treatment assembly 102 may include means for flowing the stream of gases through the air treatment assembly 102 and over and/or through the adsorbent, where the adsorbent adsorbs the pollutant and/or gas from the stream of gases during the adsorption phase over a first time period.
  • the air treatment assembly 102 may include means for flowing the regeneration gas flow over the adsorbent for purging a portion of the pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow.
  • the air treatment assembly 102 may include means for cycling between the adsorption phase and the regeneration phase, where one cycle may comprise one adsorption phase followed by one regeneration phase.
  • One cycle period may comprise the total time elapsed during a complete cycle or summation of the first time period, and the second time period.
  • a complete regeneration phase may comprise a time period for removing substantially all of the pollutant and/or gas that can be removed from the adsorbent during the regeneration phase.
  • a complete adsorption phase may comprise a time period for substantially saturating all the adsorbent during the adsorption. The duration of at least one of the following may be limited: the first time period to a period of time which is less than the complete adsorption phase and the second time period to a period of time which is less than the complete regeneration phase.
  • the means for cycling may comprise a processor and a non-transitory machine-readable medium storing instructions having computer instructions operating thereon for controlling cycling between the adsorption and regeneration phases (for example).
  • the means for cycling may comprise a control unit (not shown), such as an automated electromechanical control unit that determines when to open or close the dampers shown in FIG. 3 , for example, when to activate fans of FIG. 3 , for example, and may be responsible for flowing the incoming air purge gas through the system, for example.
  • the air management system 100 of FIGS. 1 A- 1 C and air management system 200 of FIGS. 2 A- 2 B may also operate with sensors and actuators or any other suitable elements configured for determining when to activate the cycling means.
  • the means for flowing the stream of gases through the scrubber and the means for flowing the regeneration gas flow may comprise any suitable means.
  • the means may comprise dampers, fans, (such as shown in FIG. 3 ), valves, and/or shutters and ducts, inlets and outlets (such as shown in FIGS. 1 A- 3 ) and/or conduits.
  • the following analysis may be performed for determining the duration of the limited time period.
  • the analysis is described in reference to a pollutant comprising CO 2 , but is applicable to any other pollutants.
  • a general rationale for incomplete regeneration is as follows: If the rate of release of CO 2 slows down to a trickle, the adsorbent is nearing its clean state and can already be put to work effectively, so just like there is no reason to let the adsorbent idle, there is no reason to spend too much time regenerating it to the last few percent of capacity. The question is, what is the right time to stop regeneration and to switch back to adsorption.
  • the rate of release of CO 2 is denoted by R(t), measured in units of mass per time (such as moles per minute, grams per second, etc.), where t denotes the time measured from the beginning of the regeneration cycle.
  • R(t) increases at the beginning of the regeneration cycle as the adsorbent is heated while it is still loaded with CO 2 but soon thereafter starts declining over time, as the amount of captured CO 2 declines during the regeneration cycle, and thus, R(t) gradually trails off over an extended period.
  • A(t) is the rate at which CO 2 is removed from the air flow, again measured in units of mass per time, and in analogy to R(t), it generally decreases as a function of time.
  • the typical cycle would have the adsorption phase continue for a time period of t a and then have the regeneration phase continue for a period t r . Since the amounts of carbon adsorbed and released have to balance each other in repeated cycles over the long run, it may be that the total amount adsorbed in a single adsorption phase, C, equals the amount released in a single regeneration phase, namely:
  • T The length of the entire adsorption-regeneration cycle
  • t s is the optional switchover or pause time between adsorption phase and regeneration phase; for example, time allowed for the adsorbent to cool down or warm up as needed.
  • the optimal choice of t r for any particular set of conditions in terms of temperature, flow rates and CO 2 concentrations, may be approximately identified.
  • equations (2) and (1) into (3) the following is received:
  • the maximum value forp is obtained by taking its derivative with respect to t r and equating it to zero, namely
  • Admittedly equation (12) is still not an explicit closed form expression that allows calculation of t r , but it is a useful design condition, and it does immediately suggest a lower bound, since ⁇ is always greater than 1. That means that at a minimum, it may be economically preferable to stop regeneration before the instantaneous rate R(t) drops below p, namely the following condition should be maintained
  • the regeneration phase may be terminated upon the regeneration rate R(t r ) of the adsorbent being between about equal to and a predetermined amount less than the productivity p of the complete regeneration phase, where productivity
  • This predetermined amount less than the productivity may be any suitable amount. In a non-limiting example, the predetermined amount may be in the range of 20-98% of the productivity p of the complete regeneration phase.
  • the regeneration phase is terminated upon a regeneration rate R(t r ) being between about equal to and about twice a productivity p of the complete regeneration phase, where productivity
  • C equals an amount of the pollutant and/or first gas adsorbed by the adsorbent from the stream of gases during one cycle and T is the duration of one cycle period.
  • a method for removing a gas component including at least one adsorbate (which may also be referred to herein as a pollutant(s) and/or a particular gas(s)) from a stream of mixed gases
  • the method may comprise one or more of: using an adsorbent material in a repeated cyclical fashion, with at least two distinct phases in each cycle, one being an adsorption phase where the adsorbate is partially removed from the streaming gas mixture onto the adsorbent, and one being a regeneration phase where the adsorbate is released from the adsorbent and carried away.
  • the duration of the regeneration phase may be substantially shorter than a complete regeneration phase, the complete regeneration phase being the time to release substantially all of the adsorbate that can be released under the temperature and flow conditions of the system.
  • At least an additional 10% of the adsorbate could be released if the regeneration phase were extended by 100%.
  • at least an additional 5% of the adsorbate could be released if the regeneration phase were extended by 100%.
  • FIG. 4 is a graph showing a method for calculating the optimal adsorption-regeneration cycle and in accordance with the formulas described hereinabove. As seen in FIG. 4 the values of the following parameters are substantially:
  • the regeneration may be stopped where R(t r ) according to formula (14) is equal or larger than 0.76 (grams per minutes) or according to formula (16) where R(t r ) is substantially equal to 1.52 (grams per minutes).
  • the following may be determined: the amount of the pollutant in the scrubbed air flow and/or the ability of the adsorbent to capture an additional amount of the pollutant over and above a predetermined amount, and when the amount of the pollutant is greater than a predetermined amount, and/or the adsorbent has captured the predetermined amount of the pollutant, streaming of the regeneration air flow over and/or through the adsorbent is performed.
  • the amount of the pollutant in the scrubbed air flow and/or the ability of the adsorbent to capture an additional amount of the at least one pollutant may be determined in any suitable manner, such as by a computer including a processor and a non-transitory machine-readable medium (for example).
  • This predetermined amount of the pollutant may be any suitable amount.
  • the predetermined amount may be an amount of the pollutant that substantially saturates the adsorbent. In a non-limiting example, the predetermined amount may be less than the amount of the pollutant that substantially saturates the adsorbent.
  • a level of an adsorption efficiency where the adsorption efficiency at any point in time during the one cycle has a value of 1 - C in /C out .
  • C in is the concentration of the pollutant in the incoming air flow
  • C out is the concentration of the pollutant in the outgoing air flow.
  • the adsorption efficiency value and the initial adsorption efficiency value may be determined in any suitable manner, such as by a computer including a processor and a non-transitory machine-readable medium (for example).
  • a regeneration air flow is streamed through the air treatment assembly 102 and over and/or through the adsorbent in a second direction opposite to the first direction of the incoming air, such that the regeneration air flow regenerates at least some of the adsorbent and purges at least some of the pollutants from the adsorbent.
  • streaming of the regeneration air flow over and/or through the adsorbent is performed where the adsorption efficiency value is at least about 20% less than the initial adsorption efficiency value. In some embodiments, streaming of the regeneration air flow over and/or through the adsorbent is performed where the adsorption efficiency value is at least about 30% less than the initial adsorption efficiency value. In some embodiments, streaming of the regeneration air flow over and/or through the adsorbent is performed where the adsorption efficiency value is at least about 50% less than the initial adsorption efficiency value. In some embodiments, streaming of the regeneration air flow over and/or through the adsorbent is performed where the adsorption efficiency value is at least about 80% less than the initial adsorption efficiency value.
  • the air treatment assembly 102 described above in reference to FIGS. 1 A- 4 may be configured to treat any stream of gas, such as air from the enclosed environment 110 , flue gases, or nitrogen with elevated levels of carbon dioxide, organic contaminants relative to substantially unpolluted air, or outside air.
  • any stream of gas such as air from the enclosed environment 110 , flue gases, or nitrogen with elevated levels of carbon dioxide, organic contaminants relative to substantially unpolluted air, or outside air.
  • implementations of some of embodiments disclosed may be realized in digital electronic circuitry, integrated circuitry, specially designed ASICs (application specific integrated circuits), computer hardware, firmware, software, and/or combinations thereof.
  • ASICs application specific integrated circuits
  • These various implementations may include implementation in one or more computer programs that are executable and/or interpretable on a programmable system including at least one programmable processor, which may be special or general purpose, coupled to receive data and instructions from, and to transmit data and instructions to, a storage system, at least one input device, and at least one output device.
  • Such computer programs include machine instructions/code for a programmable processor, for example, and may be implemented in a high-level procedural and/or object-oriented programming language, and/or in assembly/machine language.
  • machine-readable medium refers to any computer program product, apparatus and/or device (e.g., non-transitory mediums including, for example, magnetic discs, optical disks, flash memory, Programmable Logic Devices (PLDs)) used to provide machine instructions and/or data to a programmable processor, including a machine-readable medium that receives machine instructions as a machine-readable signal.
  • machine-readable signal refers to any signal used to provide machine instructions and/or data to a programmable processor.
  • the subject matter described herein may be implemented on a computer having a display device (e.g., a CRT (cathode ray tube) or LCD (liquid crystal display) monitor and the like) for displaying information to the user and a keyboard and/or a pointing device (e.g., a mouse or a trackball, touchscreen) by which the user may provide input to the computer.
  • a display device e.g., a CRT (cathode ray tube) or LCD (liquid crystal display) monitor and the like
  • a keyboard and/or a pointing device e.g., a mouse or a trackball, touchscreen
  • this program can be stored, executed and operated by the dispensing unit, remote control, PC, laptop, smart-phone, media player or personal data assistant (“PDA”).
  • PDA personal data assistant
  • Other kinds of devices may be used to provide for interaction with a user as well.
  • feedback provided to the user may be any form of sensory feedback (e.g., visual feedback, auditory feedback,
  • Certain embodiments of the subject matter described herein may be implemented in a computing system and/or devices that includes a back-end component (e.g., as a data server), or that includes a middleware component (e.g., an application server), or that includes a front-end component (e.g., a client computer having a graphical user interface or a Web browser through which a user may interact with an implementation of the subject matter described herein), or any combination of such back-end, middleware, or front-end components.
  • the components of the system may be interconnected by any form or medium of digital data communication (e.g., a communication network). Examples of communication networks include a local area network (“LAN”), a wide area network (“WAN”), and the Internet.
  • LAN local area network
  • WAN wide area network
  • the Internet the global information network
  • the computing system may include clients and servers.
  • a client and server are generally remote from each other and typically interact through a communication network.
  • the relationship of client and server arises by virtue of computer programs running on the respective computers and having a client-server relationship to each other.
  • features from one and/or another disclosed embodiment may be interchangeable with features from other disclosed embodiments, which, in turn, correspond to yet other embodiments.
  • one or more features/elements of disclosed embodiments may be removed and still result in patentable subject matter (and thus, resulting in yet more embodiments of the subject disclosure).

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Abstract

Some embodiments of the disclosure correspond to, for example, a method for controlling a scrubber containing an adsorbent. The scrubber may be configured to cycle between scrubbing at least one pollutant/gas from a stream of gases with the pollutant/gas being adsorbed onto the adsorbent, and regenerating at least some of the adsorbent and thereby purging at least some of the one pollutant and/or first gas from the adsorbent via a regeneration gas flow. The method may include flowing a stream of gases through the scrubber, the scrubber including the adsorbent and adsorbing at least some of the one pollutant/gas from the stream of gases onto the adsorbent during an adsorption phase over a first time period. The method may also include purging at least a portion of the one pollutant/ gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and cycling therebetween. Some other embodiments of the disclosure, for example, include an air treatment assembly which includes an adsorbent for adsorbing at least on pollutant/gas from a flow of air in one direction, and purging at least some of the adsorbed pollut -ant/gas from the adsorbent with a regeneration air flow to regenerate the adsorbent.

Description

    CROSS REFERENCE TO RELATED APPLICATIONS
  • This application claims priority to: U.S. Provisional Pat. Application No. 61/650204, filed May 22, 2012 and entitled “Air Management Systems with Integrated Ventilation and Scrubbing Functionality”; U.S. Provisional Pat. Application No. 61/664168, filed Jun. 26, 2012 and entitled “Optimal Adsorption-Regeneration Cycle for Indoor Air Scrubbing”; U.S. Provisional Pat. Application No. 61/664748, filed Jun. 27, 2012 and entitled “Optimal Adsorption-Regeneration Cycle for Indoor Air Scrubbing”; U.S. Provisional Pat. Application No. 61/704796, filed Sep. 24, 2012 and entitled “Air Management Systems”. The disclosures of the above applications are incorporated herein by reference in their entireties.
  • TECHNICAL FIELD
  • Embodiments of the present disclosure generally relate to air management systems and particularly to air management systems including adsorbent based air treatment systems.
  • BACKGROUND
  • Heating, Ventilation and Air-Conditioning (“HVAC”) systems provide circulation of indoor air in enclosed environments, including buildings and structures of all kinds, vehicles, and vessels. The HVAC system’s primary role is to maintain comfortable temperature and humidity, as well as good indoor air quality. In order to maintain good air quality, the circulating air should be refreshed, either by continually replacing it with fresh air from outside the enclosed environments, or by treating it for removal of unwanted contaminants that tend to form or buildup in the enclosed environments. The contaminants may also be referred to as pollutants, or substances. These pollutants may include carbon dioxide (CO2) as well as volatile organic compounds (VOCs), inorganic gases like sulfur oxides, nitrous oxides, carbon monoxide, radon and others. Particles and microorganisms also represent non-gaseous pollutants that affect indoor air quality and should be filtered or removed. Since replacement of indoor air may not provide a satisfactory solution - whether due to the thermal load it imposes on the HVAC system, or due the poor air quality of the outside air, or lack of access to outside fresh air, indoor air may be treated by means of adsorbents to remove gas pollutants.
  • As adsorbents collect pollutants from the air, they gradually become saturated and lose their adsorptive efficiency. In order to use adsorbents for an extended service period, it is often necessary to periodically purge them in a process known as regeneration. Regeneration may be performed by streaming a purge gas (which may also be referred to as a regeneration gas) over and/or through the adsorbent. For example, the adsorbent may be flushed with air or some other gas that has a higher temperature and/or lower partial pressure of pollutants, or by heating the adsorbent itself, whereby the pollutant molecules are carried off the adsorbent surface. Thus, adsorbents are often used in an adsorption- desorption “swing cycle” where in the adsorption, or cleaning, part of the cycle, they capture certain species of gases, and continue to do so until the adsorbent reaches saturation. During desorption, or a regeneration cycle, they release the gases which were adsorbed until they recover their original capacity and adsorption efficiency, at which point a new cycle can begin. The swing cycle can be at least one of, for example, a temperature-swing cycle, pressure-swing cycle, or a concentration-swing adsorption cycle. In some cases both temperature and concentration, or temperature and pressure, may be changed during regeneration.
  • The use of regenerable adsorbents for removing carbon dioxide (CO2) and VOCs in indoor air, relying on a swing cycle is an important alternative to air replacement, especially when the outside conditions make air replacement energetically costly, environmentally undesirable or otherwise impractical. However regeneration economics and performance are critical, as regeneration represents downtime for the air treatment function and energy must be consumed to flow the purge gas and release the pollutants. Finding the optimal economic and functional performance is further complicated by varying conditions of pollutant species and concentration levels, as well as temperature and flow rates.
  • SUMMARY OF DISCLOSURE
  • In some embodiments of the present disclosure systems and methods are described for removal of CO2 and other pollutants from indoor air using adsorbents and a temperature-or concentration-swing adsorption cycle.
  • In some embodiments of the present disclosure reversing the direction of flow during regeneration can provide advantages when one type of pollutant is present and when more than one type of pollutant is present.
  • In accordance with some embodiments there is provided a method for reducing the level of at least one pollutant contained in indoor air from a human-occupied, enclosed environment. The method may comprise providing an air treatment assembly including at least one type of adsorbent, the adsorbent may be configured for capturing at least one pollutant entrained in an indoor air flow from the enclosed environment and regenerating upon exposure to a regenerating gas flow; streaming the indoor air flow over and/or through the adsorbent in a first direction such that the adsorbent captures at least some of the pollutant from the indoor air flow, where after being flowed over and/or through the adsorbent, the air flow comprises a scrubbed air flow; and streaming the regeneration gas flow over and/or through the adsorbent in a second direction opposite to the first direction, such that the regeneration gas flow regenerates at least some of the adsorbent and purges at least some of the pollutant from the adsorbent.
  • In accordance with some embodiments the air treatment assembly comprises at least two adsorbents such that the streaming indoor air flows through a first adsorbent and subsequently through a second adsorbent, and that as a result of the reversal of the flow direction during regeneration, substances purged from the first adsorbent do not flow across the second adsorbent.
  • In accordance with some embodiments, pollutants may be released from the one adsorbent during regeneration and may accumulate in the air treatment assembly or air conduits attached to it, and as a result of the reversal of the flow direction during regeneration, the released pollutants are substantially prevented from accumulating downstream from the adsorbent and accumulate substantially in sections of the air treatment assembly that are upstream from the adsorbent, the air treatment assembly may comprise an inlet for indoor air flowing through the adsorbent and upstream the adsorbent being in greater proximity to the inlet than downstream the adsorbent.
  • In accordance with some embodiments the pollutant and/or first gas may be selected from the group consisting of: carbon dioxide, volatile organic compounds, sulfur oxides, radon, nitrous oxides and carbon monoxide. The adsorbent may comprise at least one of an amine supported by a solid, activated carbon, clay, carbon fibers, silica, alumina, zeolites, molecular sieves, titanium oxide, polymer, porous polymers, polymer fibers and metal organic framework. The supporting solid may be at least one of silica, carbon, clay or metal oxide. The adsorbent may comprise granular solids or pelleted shaped solids.
  • In accordance with some embodiments there is provided a computer implemented method for reducing the level of at least one pollutant contained in indoor air from an enclosed, human-occupied environment. The method may comprise streaming an indoor air flow over and/or through an adsorbent provided within an air treatment assembly in a first direction, the indoor air flow containing at least one pollutant from inside the enclosed environment, such that the adsorbent captures at least some of the pollutant from the indoor air, where after being flowed over and/or through the adsorbent, the air flow comprises a scrubbed air flow, determining a level of an adsorption efficiency, where the adsorption efficiency at any point in time during the one cycle has a value of 1 - Cin/Cout, where Cin is the concentration of the pollutant in the incoming air flow and Cout is the concentration of the pollutant in an outgoing air flow, and where an initial adsorption efficiency value is the adsorption efficiency value at the beginning of the adsorption phase, where the adsorption efficiency value is less than the initial adsorption efficiency value, streaming a regeneration air flow through the air treatment assembly and over and/or through the adsorbent in a second direction opposite to the first direction, such that the regeneration air flow regenerates at least some of the adsorbent and purges at least some of the at least one pollutant from the adsorbent, where at least one of the above is performed by a processor.
  • In accordance with some embodiments there is provided a system for reducing the level of at least one pollutant contained in indoor air from an enclosed, human-occupied environment. The method may comprise an air treatment assembly including an adsorbent, the adsorbent may be configured for capturing at least one pollutant entrained in an indoor air flow and regenerating upon exposure to a regenerating gas flow; and streaming means for streaming the indoor air flow over and/or through the adsorbent in a first direction, such that the adsorbent captures at least some of the at least one pollutant from the indoor air flow, and streaming the regeneration air flow over and/or through the adsorbent in a second direction opposite to the first direction, such that the regeneration gas flow regenerates at least some of the adsorbent and purges at least some of the pollutant from the adsorbent.
  • In accordance with some embodiments there is provided a system for reducing the level of at least one pollutant contained in indoor air from an enclosed, human-occupied environment. The system may comprise an air treatment assembly including an adsorbent, the adsorbent configured for capturing at least one pollutant entrained in an indoor air flow and regenerating upon exposure to a regenerating gas flow, streaming means for streaming the indoor air flow over and/or through the adsorbent in a first direction, and/or for streaming the regeneration gas flow over and/or through the adsorbent in a second direction opposite to the first direction; at least one processor; a non-transitory machine-readable medium storing instructions that, when executed by the processor, perform the method, which may comprise: streaming the indoor air over and/or through the adsorbent in the first direction such that the adsorbent captures at least some of the pollutant from the indoor air; and determining a level of an adsorption efficiency, where the adsorption efficiency at any point in time during the one cycle has a value of 1 - Cin/Cout, where Cin is the concentration of the pollutant in the incoming air flow and Cout is the concentration of the pollutant in an outgoing air flow, and where an initial adsorption efficiency value is the adsorption efficiency value at the beginning of the adsorption phase, where the adsorption efficiency value is less than the initial adsorption efficiency value, streaming of the regeneration gas flow over and/or through the adsorbent is performed.
  • In some embodiments, a method for controlling a scrubber containing an adsorbent, the scrubber configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the at least one pollutant and/or first gas being adsorbed onto the adsorbent, and regenerating at least some of the adsorbent and thereby purging at least some of the at least one pollutant and/or first gas from the adsorbent via a regeneration gas flow. The method may comprise flowing a stream of gases through the scrubber, the scrubber comprising the adsorbent, adsorbing at least some of the one pollutant and/or first gas from the stream of gases onto the adsorbent during an adsorption phase over a first time period, purging a portion of the at least one pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and cycling between the adsorption phase and the regeneration phase. The method may also include limiting at least one of: the duration of the first time period to a period of time which is less than the time required to have the adsorbent adsorb as much of the pollutant/gas as the adsorbent can adsorb complete adsorption phase, and the duration of the second time period to a period of time which is less than the time required to completely regenerate the adsorbent.
  • In accordance with some embodiments there is provided a method for reducing the level of at least one pollutant contained in indoor air from an enclosed, human-occupied environment. The method may comprise providing an air treatment assembly including an adsorbent, the adsorbent configured for capturing at least one pollutant entrained in an indoor air flow from the enclosed environment and regenerating upon exposure to a regenerating gas flow streaming the indoor air flow over and/or through the adsorbent in a first direction such that the adsorbent captures at least some of the at least one pollutant from the indoor air flow, where the streaming of the indoor air flow over and/or through the adsorbent comprises an adsorption phase; and streaming the regeneration gas flow over and/or through the adsorbent in a second direction opposite to the first direction, such that the regeneration air flow regenerates at least some of the adsorbent and purges at least some of the at least one pollutant from the adsorbent, where the streaming of the regeneration gas flow over and/or through the adsorbent comprises a regeneration phase, cycling between the adsorption phase and the regeneration phase, where one cycle comprises an adsorption phase followed by a regeneration phase, one cycle period comprises the total time elapsed during one cycle; the at least one pollutant purged from the adsorbent is carried away by the regeneration gas flow, and a complete regeneration phase comprises a time period for removing substantially all of the at least one pollutant from the adsorbent during the regeneration phase, and a complete adsorption phase comprises a time period for substantially saturating all the adsorbent during the adsorption; and limiting at least one of: the duration of the first time period to a period of time which is less than the complete adsorption phase, and the duration of the second time period to a period of time which is less than the complete regeneration phase.
  • In accordance with some embodiments prior to streaming the regeneration gas flow the method may further include determining a level of an adsorption efficiency, where the adsorption efficiency at any point in time during the one cycle has a value of 1 - Cin/Cout, where Cin is the concentration of the pollutant in the incoming air flow and Cout is the concentration of the pollutant in an outgoing air flow, and where an initial adsorption efficiency value is the adsorption efficiency value at the beginning of the adsorption phase, where the adsorption efficiency value is less than the initial adsorption efficiency value, streaming of the regeneration gas flow over and/or through the adsorbent is performed.
  • In accordance with some embodiments the adsorption efficiency value is at least about 20% less than the initial adsorption efficiency value. In accordance with some embodiments the adsorption efficiency value is at least about 30% less than the initial adsorption efficiency value. In accordance with some embodiments the adsorption efficiency value is at least about 50% less than the initial adsorption efficiency value. In accordance with some embodiments the adsorption efficiency value is at least about 80% less than the initial adsorption efficiency value.
  • In some embodiments of the present disclosure a key for optimal system economics is to terminate the regeneration phase and the adsorption phase before they are complete, as the rates of adsorption and desorption decline. A detailed analysis shows how to identify and set the optimal points at which to switch over from regeneration to adsorption and vice versa.
  • In accordance with some embodiments there is provided a method for controlling a scrubber containing an adsorbent, the scrubber may be configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the pollutant and/or first gas being adsorbed onto the adsorbent, and regenerating at least some of the adsorbent and thereby purging at least some of the pollutant and/or first gas from the adsorbent via a regeneration gas flow. The method may include flowing a stream of gases through the scrubber, the scrubber comprising the adsorbent; adsorbing at least some of the pollutant and/or first gas from the stream of gases onto the adsorbent during an adsorption phase over a first time period; purging a portion of the pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and cycling between the adsorption phase and the regeneration phase. One cycle may comprise at least an adsorption phase followed by a regeneration phase, one cycle period may comprise the total time elapsed during one cycle. The pollutant and/or first gas purged from the adsorbent may be carried away by the regeneration gas flow. A complete regeneration phase may comprise a time period for removing substantially all of the pollutant and/or first gas from the adsorbent during the regeneration phase, and a complete adsorption phase may comprise a time period for substantially saturating all the adsorbent during the adsorption. The method may include limiting at least one of: the duration of the first time period to a period of time which is less than the complete adsorption phase, and/or the duration of the second time period to a period of time which is less than the complete regeneration phase.
  • In accordance with some embodiments, the first time period may comprise about 95% of a complete adsorption phase. In accordance with some embodiments, the first time period is about 90% of a complete adsorption phase. In accordance with some embodiments, the first time period is about 80% of a complete adsorption phase. In accordance with some embodiments, the first time period is about 50% of a complete adsorption phase. In accordance with some embodiments, the first time period is about 20% of a complete adsorption phase. In accordance with some embodiments, the first time period comprises about 20% to about 95% of a complete adsorption phase.
  • In accordance with some embodiments, the second time period comprises about 95% of a complete regeneration phase. In accordance with some embodiments, the second time period is about 90% of a complete regeneration phase. In accordance with some embodiments, the second time period is about 80% of a complete regeneration phase. In accordance with some embodiments, the second time period is about 50% of a complete regeneration phase. In accordance with some embodiments, the second time period is about 20% of a complete regeneration phase. In accordance with some embodiments, the second time period comprises about 20% to about 95% of a complete regeneration phase.
  • In accordance with some embodiments, the regeneration phase may be terminated upon a regeneration rate R(tr) of the adsorbent being between about equal to and a predetermined amount less than a productivity p of the complete regeneration phase, where productivity
  • p = C T ,
  • and C equals an amount of the pollutant and/or first gas adsorbed by the adsorbent from the stream of gases during one cycle and T is the duration of one cycle period.
  • In accordance with some embodiments, the regeneration phase is terminated upon a regeneration rate R(tr) being between about equal to and about twice a productivity p of the complete regeneration phase, where productivity
  • p = C T ,
  • and C equals an amount of the pollutant and/or first gas adsorbed by the adsorbent from the stream of gases during one cycle and T is the duration of one cycle period.
  • In accordance with some embodiments, the pollutant and/or first gas may be selected from the group consisting of: carbon dioxide, volatile organic compounds, sulfur oxides, radon, nitrous oxides and carbon monoxide. The adsorbent may comprise at least one of: an amine supported by a solid, activated carbon, clay, carbon fibers, silica, alumina, zeolites, molecular sieves, titanium oxide, polymer, porous polymers, polymer fibers and metal organic frameworks. The supporting solid may be at least one of silica, carbon, clay or metal oxide. The adsorbent may comprise granular solids or pelleted shaped solids. The stream of gases may comprise air from an enclosed environment, outdoor air, flue gases, or nitrogen with elevated levels of carbon dioxide or organic contaminants, relative to substantially unpolluted air.
  • In accordance with some embodiments, the one cycle may further comprise at least one of: (i) a first switchover phase prior to the regeneration phase, and (ii) a second switchover phase following the regeneration phase. The second switchover phase may comprise a period of time to bring the adsorbent to a temperature to adsorb pollutant and/or first gas during the adsorption phase. The first switchover phase may comprise a period of time to bring the adsorbent to a temperature to release the at least one pollutant and/or first gas from the adsorbent during the regeneration phase.
  • In accordance with some embodiments, prior to streaming the regeneration gas flow the method may further include determining a level of an adsorption efficiency, where the adsorption efficiency at any point in time during the one cycle has a value of 1 - Cin/Cout, where Cin is the concentration of the pollutant in the incoming air flow and Cout is the concentration of the pollutant in an outgoing air flow, and where an initial adsorption efficiency value is the adsorption efficiency value at the beginning of the adsorption phase. The adsorption efficiency value is less than the initial adsorption efficiency value, streaming of the regeneration gas flow over and/or through the adsorbent is performed.
  • In accordance with some embodiments there is provided a system for controlling a scrubber, the system may comprise a scrubber containing an adsorbent, the scrubber may be configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the at least one pollutant and/or first gas being adsorbed onto the adsorbent, and purging the at least one pollutant and/or first gas from the adsorbent via a regeneration gas flow; means for flowing the stream of gases through the scrubber and over and/or through the adsorbent, where the adsorbent adsorbs at least one pollutant and/or first gas from the stream of gases during an adsorption phase over a first time period; means for flowing the regeneration gas flow over the adsorbent for purging a portion of the pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and means for cycling between the adsorption phase and the regeneration phase. One cycle may comprise one adsorption phase followed by one regeneration phase. One cycle period may comprise the total time elapsed during one cycle. The pollutant and/or first gas purged from the adsorbent may be carried away by the regeneration gas flow. A complete regeneration phase may comprise a time period for removing substantially all of the pollutant and/or first gas from the adsorbent during the regeneration phase. A complete adsorption phase comprises a time period for substantially saturating all the adsorbent during the adsorption. The duration of at least one of the following may be limited: the duration of the first time period to a period of time which is less than the complete adsorption phase, and the duration of the second time period to a period of time which is less than the complete regeneration phase.
  • In accordance with some embodiments, the means for cycling may comprise a processor and a non-transitory machine-readable medium storing instructions (for example), having computer instructions/code operating thereon for controlling cycling between the adsorption and regeneration phases.
  • In accordance with some embodiments there is provided a computer implemented method for controlling a scrubber containing an adsorbent, the scrubber may be configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the at least one pollutant and/or first gas being adsorbed onto the adsorbent, and purging the at least one pollutant and/or first gas from the adsorbent via a purging gas flow, the method comprising: flowing a stream of gases through the scrubber, the scrubber including or comprising an adsorbent; adsorbing at least one pollutant and/or first gas from the stream of gases onto the adsorbent during an adsorption phase over a first time period, purging a portion of the at least one pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and cycling between the adsorption phase and the regeneration phase. One cycle may comprise one adsorption phase followed by one regeneration phase. One cycle period may comprise the total time elapsed during one cycle. At least one pollutant and/or first gas purged from the adsorbent may be carried away by the regeneration gas flow. A complete regeneration phase comprises a time period for removing substantially all of the pollutant and/or first gas from the adsorbent during the regeneration phase. A complete adsorption phase may comprise a time period for substantially saturating all the adsorbent during the adsorption. The method may include limiting at least one of: the duration of the first time period to a period of time which is less than the complete adsorption phase, and the duration of the second time period to a period of time which is less than the complete regeneration phase, where at least one of the above is performed by at least one processor.
  • In accordance with some embodiments there is provided a system for controlling a scrubber containing an adsorbent, the scrubber may be configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the pollutant and/or first gas being adsorbed onto the adsorbent, and purging the pollutant and/or first gas from the adsorbent via a regeneration gas flow. The system may comprise at least one processor and a non-transitory machine-readable medium storing instructions that, when executed by the at least one processor, perform the method which may comprise: flowing a stream of gases over and/or through the adsorbent, where the adsorbent adsorbs at least some of the pollutant and/or first gas from the stream of gases during an adsorption phase over a first time period; purging a portion of the pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and cycling between the adsorption phase and the regeneration phase. One cycle may comprise one adsorption phase followed by one regeneration phase. One cycle period may comprise the total time elapsed during one cycle. At least one pollutant and/or first gas purged from the adsorbent may be carried away by the regeneration gas flow. A complete regeneration phase comprises a time period for removing substantially all of the pollutant and/or first gas from the adsorbent during the regeneration phase. A complete adsorption phase may comprise a time period for substantially saturating all the adsorbent during the adsorption. The method may include limiting at least one of: the duration of the first time period to a period of time which is less than the complete adsorption phase, and the duration of the second time period to a period of time which is less than the complete regeneration phase.
  • BRIEF DESCRIPTION OF THE DRAWINGS
  • The principles and operations of the systems, apparatuses and methods according to some embodiments of the present disclosure may be better understood with reference to the drawings, and the following description. These drawings are given for illustrative purposes only and are not meant to be limiting.
  • FIGS. 1A-1C are each a schematic illustration of an air management system according to some embodiments of the present disclosure;
  • FIGS. 2A and 2B are each a schematic illustration of an air management system according to some embodiments of the present disclosure;
  • FIG. 3 is a schematic illustration of an air treatment assembly according to some embodiments of the present disclosure; and
  • FIG. 4 is a graph showing an adsorption-regeneration cycle according to some embodiments of the present disclosure.
  • DETAILED DESCRIPTION
  • Removing carbon dioxide (CO2) and volatile organic compounds (VOCs) from indoor air, or reducing the level of at least one pollutant or a gas contained in indoor air from an enclosed environment, can pave the way for improved indoor air quality and lower energy costs in enclosed environments. In some embodiments, adsorbents, such as solid adsorbents, are used to scrub unwanted pollutants including gases and vapors, from indoor air, namely pollutants entrained in an indoor air flow from the enclosed environment. Adsorbents selective to CO2 are known in the art and include, but are not limited to, various types of amines and solid-supported amines, as well as clays, molecular sieves, zeolites, various forms of silica and alumina, various forms of carbon, activated carbon, carbon fibers, titanium oxide, porous polymers, polymer fibers and metal organic frameworks.
  • Adsorbents selective to VOCs may include molecular sieves, activated carbon, zeolites, carbon fibers and carbon particles, for example. In some embodiments more than one type of adsorbent is used.
  • In some embodiment there may be a first layer or bed of an adsorbent for capturing CO2, and a second layer of an adsorbent for capturing VOCs, positioned downstream from the first layer, relative to the direction of the air flow of incoming indoor air. In some embodiments, the first layer may comprise solid supported amines for capturing CO2, and the second layer may comprise carbon adsorbents for capturing VOCs.
  • FIGS. 1A-1C are each a schematic illustration of an air management system 100 including a scrubber, which may be referred to as an air treatment assembly 102. The air management system 100 may include an air circulation system, such as a central HVAC system 108 provided to manage and circulate indoor air within an enclosed environment 110.
  • The enclosed environment 110 may comprise an office building, a commercial building, a bank, a residential building, a house, a school, a factory, a hospital, a store, a mall, an indoor entertainment venue, a storage facility, a laboratory, a vehicle, an aircraft, a ship, a bus, a theatre, a partially and/or fully enclosed arena, an education facility, a library and/or other partially and/or fully enclosed structure and/or facility which can be at times occupied by equipment, materials, live occupants (e.g., humans, animals, synthetic organisms, etc.) and/or any combination thereof.
  • The HVAC system 108 shown in FIGS. 1A-1C may comprise an air handling unit 114 in fluid communication with the enclosed environment 110. The air handling unit 114 may provide air circulation to various parts of the enclosed environment 110 by means of ducts 116 or conduits, as shown in FIGS. 1A-1C. The air handling unit 114 may include any suitable configuration for conditioning the temperature and humidity of the air flowing through it. Conditioned air exiting the air handling unit 114 may be provided to the enclosed environment 110 as supply air 118. Return air 120, which is indoor air 120 from the enclosed environment 110, may exit the enclosed environment 110 via ducts 122 or a plenum or any other suitable means.
  • In some embodiments, a portion of the return air 120 may be exhausted as exhaust air 124, directly or via ducts 126. Outside, fresh air 130 may be introduced into the air handling unit 114 via ducts 132.
  • The air treatment assembly 102 may be placed in any suitable location within the enclosed environment relative to the air management system 100 and is configured to receive at least a portion of the indoor air. In some embodiments, as shown in FIG. 1A, the air treatment assembly 102 is placed in parallel to the air handling unit 114. A portion of the return air 120 may flow to the air treatment assembly 102 and thereafter to the air handling unit 114 and the remaining portion may flow directly to the air handling unit 114 and/or may be exhausted as exhaust air 124, via ducts 126.
  • In some embodiments, as shown in FIG. 1B, the air treatment assembly 102 is placed in series with the air handling unit 114, either upstream relative to the air handling unit 114 or downstream thereof. A portion of the return air 120 may flow to the air treatment assembly 102 and thereafter to the air handling unit 114 and a portion may be exhausted as exhaust air 124, via ducts 126.
  • In some embodiments, as shown in FIG. 1C, the air treatment assembly 102 is not in direct fluid communication with the air handling unit 114, and may be placed within the enclosed environment 110. A portion of circulating indoor air 120 may flow into the air treatment assembly 102 and thereout, back into the enclosed environment 110.
  • FIGS. 2A and 2B are each a schematic illustration of an air management system 200 comprising the air treatment assembly 102. The air management system 200 may include a distributed air circulation system 208 comprising one or more fan-coil units 210 provided to manage and circulate indoor air within the enclosed environment 110.
  • In some embodiments, as seen in FIGS. 2A and 2B, the enclosed environment 110 may comprise a plurality of rooms 220. A fan-coil unit 210 may be placed in one or more of the rooms 220. An air treatment assembly 102 may be placed in one or more of the rooms 220. At least a portion of return air 120, comprising indoor air from the room 220, may flow into the air treatment assembly 102 and a separate stream of air may flow into the fan-coil unit 210 and/or may be exhausted out of the room 220.
  • The air treatment assembly 102 may be placed at any suitable location. In some embodiments, as shown in FIG. 2A, scrubbed air flowing out of the air treatment assembly 102 may flow directly to the fan-coil unit 210 via a duct 222.
  • In some embodiments, as shown in FIG. 2B, the air treatment assembly 102 may not be in direct fluid communication with the fan-coil unit 210. At least a portion of indoor air 120 may flow into the air treatment assembly 102 and a portion may flow into the fan-coil unit 210.
  • In accordance with some embodiments, as seen in FIG. 3 , the air treatment assembly 102 may be provided to reduce the concentration of unwanted substances or pollutants present in the air introduced therein. The air treatment assembly 102 may comprise one or more adsorbent beds or layers for one or more types of pollutants. For example, a first adsorbent 230 may be provided for capturing gas pollutants, such as CO2 and a second adsorbent 234 may be provided for capturing other gas pollutants, such as VOCs. Examples of air treatment assemblies are disclosed in applicant’s U.S. Pat. No. 8157892, which is incorporated herein by reference in its entirety.
  • The CO2 adsorbent 230 may comprise a solid supported amine, such as disclosed in applicant’s PCT application PCT/US12/38343, which is incorporated herein by reference in its entirety.
  • In the example of FIG. 3 , the first adsorbent 230 may be formed of an adsorbent bed comprising adsorbent particles 236. The adsorbent particles 236 may comprise solid supported amines or any other adsorbent material, in any suitable form, such as granular solids or pelleted shaped solids, for example. The second adsorbent 234 may be formed of a layer 238 comprising a carbon cloth or any other suitable material.
  • During scrubbing, the air treatment assembly 102 may operate in a cycle comprising an adsorption phase and a regeneration phase. In the adsorption phase the pollutants, such as the CO2 or VOCs, are first captured and adsorbed by the adsorbents, which as described above, may comprise one or more adsorbents, such as adsorbents 230 and 234. Following the capture of these pollutants in the adsorption phase, the adsorbent may be regenerated during the regeneration phase by urging the release of the pollutants therefrom.
  • The regeneration may be performed in any suitable manner. For example, regeneration may be performed by exposing, (e.g. by flushing) the adsorbent to a purge gas for purging and releasing at least a portion of the pollutants therefrom.
  • In some embodiments, the purge gas may comprise outdoor air 240. The outdoor air 240 may be heated prior to entering the air treatment assembly 102 by any suitable method, such as will be further described.
  • Incoming contaminated indoor air 120 from the enclosed environment 110 is shown in FIGS. 1A-3 as flowing in a first direction into the air treatment assembly 102 through an aperture or a first inlet 244, which may be controlled by an inlet damper 248 or any other suitable means. Scrubbed air may exit the air treatment assembly 102 via an oppositely facing aperture or second outlet 250, which may be controlled by an outlet damper 254 or any other suitable means. The incoming side is referred to as upstream and the outgoing side as downstream.
  • During the regeneration phase the outdoor air 240, shown as a dashed line, may flow into the air treatment assembly 102 via an inlet 260, which may be controlled by an inlet damper 264. The outside air 240 may flow out of the air treatment assembly 102 via an outlet 268, which may be controlled by an outlet damper 270. The inlet damper 264 and outlet damper 270 may be open during the regeneration phase while the inlet damper 248 and outlet damper 254 are generally closed.
  • During the adsorption phase the inlet damper 264 and outlet damper 270 may be closed while the inlet damper 248 and outlet damper 250 are generally open.
  • In some embodiments, the outdoor air 240 may flow into a heating subassembly 280 for heating the outdoor air 240 therein before entering the air treatment assembly 102. Heating the outdoor air 240 may be performed in any suitable manner, such as by an electrical heating coil placed within the heating subassembly 280. Additional methods for heating the outdoor air 240 include: water coils using hot water provided from a separate source; direct or indirect solar heat; a furnace using gas or other fuel; a heat pump; or any other suitable source of heat. The outdoor air 240 may be heated from the ambient temperature to any suitable temperature, typically within a range of approximately 30-120° C. Alternatively, the outdoor air 240 may be heated to a temperature less than 80° C. Alternatively, the outdoor air 240 may be heated to a temperature less than 50° C. Alternatively, the outdoor air 240 may enter the air treatment assembly 102 at the ambient temperature without prior heating thereof.
  • It is noted that the heating subassembly 280 may be placed in any suitable location. For example, the heating subassembly 280 may be placed in proximity to the air treatment assembly 102 or may be located at a certain distance whereby warm, outdoor air 240 may be delivered from the heating subassembly 280 to the air treatment assembly 102 via a conduit (not shown).
  • In accordance with an embodiment, as shown in FIGS. 1A-3 , the outdoor air 240, during the regeneration phase may flow in a second direction, which is the opposite direction of the indoor air flow during the adsorption phase (i.e. the first direction).
  • In order to enable the reverse direction of the air flow during regeneration, the air treatment assembly 102 may be configured with an appropriate fan 290 or fans that either pushes the outside air 240 into the air treatment assembly 102 near the inlet 260 or pulls the outside air 240 thereout at outlet 268, as shown in FIGS. 1A-3 . The fan 290 can be part of the air treatment assembly 102 or can be incorporated into the air heating subassembly 280 or any other suitable location within the air management system 100 of FIGS. 1A-1C or air management system 200 of FIGS. 2A and 2B.
  • The air treatment assembly 102 may comprise additional fans, such as fan 292, for pushing or pulling the return air 120 through the air treatment assembly 102.
  • In other embodiments the direction of air flow in regeneration is in the same direction of the return air flow.
  • The reverse air flow during the regeneration phase offers certain advantages which are best understood in relation to FIG. 3 and inserts thereof. During adsorption, pollutant laden air first encounters an upstream section or surface 300 of the adsorbent bed and the air is gradually depleted of CO2 or other pollutants as it advanced through the bed, away from surface 300. The adsorbent material near this surface 300 receives the most contaminated air and as a result, there is typically a higher load of captured pollutants 304 in the upstream side of the adsorbent bed, than in an oppositely facing surface 308 in the downstream side of the adsorbent bed. During regeneration, if the flow is in the same direction of the return air flow, the pollutants carried from the upstream side are forced to flow through the entire bed on their way out, and through subsequent adsorbent layers (such as layer 238) if there are such. This may increase the likelihood that some of these purged pollutants will be recaptured. If the flow is reversed, the highest concentration of pollutants is removed backwards and away from the upstream section without passing through the bed. A similar dynamic may apply also to captured dust particles 310.
  • The considerations is also significant when a dual adsorbent system is deployed, such as with the second adsorbent 234, e.g. the VOC adsorbent layer 238, downstream from the first adsorbent 230, such as the CO2 adsorbent. This is because the CO2 adsorbent may release VOCs and particles or vapors 314 during regeneration. For example, a solid supported amine based CO2 adsorbent may release some amine vapors 314 during high temperature regeneration. These vapors 314 are preferably exhausted directly and not forced to flow through the VOC adsorbent where they may be captured, thus loading and contaminating the VOC adsorbent 234 instead of allowing it to be purged and regenerated. By reversing the flow direction in regeneration, clean air passes though the VOC adsorbent 234 first and then through the CO2 adsorbent 230, so that any volatilized amines are carried away from the VOC adsorbent 234 rather than through it.
  • Furthermore, granular adsorbents 236 may release their own dust particles 310 and it is preferable to exhaust them without passing them through the air treatment assembly 102 downstream dust filter 320 or a fiber cloth, such as layer 238, where dust particles 310 can buildup and impede air flow.
  • The reverse air flow during the regeneration phase may be significant in any air treatment assembly including or comprising a single or plurality of adsorbents configured to adsorb any pollutants from incoming air.
  • In some embodiments, pollutants may be released from the adsorbent during regeneration and may accumulate in the air treatment assembly 102 or air conduits attached to it or sections of the air treatment assembly 102. As a result of the reversal of the flow direction during regeneration the released pollutants may be substantially prevented from accumulating downstream from the adsorbent and accumulate substantially in sections of the air treatment assembly that are upstream from the adsorbent. Upstream the adsorbent may also be defined as being in greater proximity to the inlet 244 than downstream the adsorbent.
  • It is noted in reference to FIGS. 1A-3 , that any other suitable means besides dampers, such as valves, fans or shutters, may be used to control the volume of air entering and/or exiting the air treatment assembly 102 or flowing the incoming air (or stream of gases) through the air treatment assembly 102. Additionally, blowers or any other suitable means for urging flow of air may be used in place of or in addition to the fans of the air treatment assembly 102.
  • It is further noted in reference to FIGS. 1A-3 , that any suitable streaming means may be provided, such as dampers, fans, (such as shown in FIG. 3 ), valves, and/or shutters and ducts inlets and outlets (such as shown in FIGS. 1A-3 ) and/or conduits. The streaming means may be used for streaming the indoor air flow over and/or through the adsorbent in the first direction, such that the adsorbent captures at least the pollutant or first gas from the indoor air flow. The streaming means may further be used for streaming the regeneration air flow over and/or through the adsorbent in the second direction opposite to the first direction, such that the regeneration gas flow regenerates at least some of the adsorbent and purges at least some of the pollutant from the adsorbent.
  • In some embodiments, the air management system 100 of FIGS. 1A-1C or air management system 200 of FIGS. 2A and 2B may include fans, and dampers or any other suitable means for circulating air therein.
  • Optimizing the Cycle Length and Regeneration Time
  • Due to the need to treat large volumes of air for extended periods of time with a finite amount of adsorbent, it is advantageous to generally continually reuse the same adsorbent by means of a temperature swing cycle or a concentration swing cycle or some combination thereof. The problem is particularly important in the case of CO2 due to its large cumulative volumes, but in principle carries over to most other gases and vapors. Generally that means that the adsorbent undergoes a cycle with several phases in each cycle. In the adsorption phase, the adsorbent selectively captures and removes certain gases from the air flow, and in the regeneration phase it releases the captured gases, presumably to a purge gas that is exhausted. During regeneration one or both of the following conditions may be met, (a) the adsorbent is warmer than it was during adsorption and/or (b) the incoming purge gas has lower partial pressure of the released pollutants.
  • As the adsorption phase progresses, the adsorbent gradually becomes saturated with CO2 (or other pollutants) and its ability to adsorb begins to degrade, eventually stopping adsorption entirely. The transition can be gradual or fairly sharp, depending on a number of parameters including the flow rate, temperature, thickness of adsorbent bed, and of course the chemistry and structural properties of the adsorbent.
  • During the regeneration phase the adsorbent is purged. The amount of adsorbed gas that is released is initially high and then gradually declines as the adsorbent is depleted from the captured gas. As the amount of gas released tapers off, a substantial fraction of the regeneration time is spent on extracting a small residual fraction of the amount of pollutants.
  • In some embodiments there may be continual scrubbing of the indoor air as it circulates. The time spent regenerating the adsorbent is time when the adsorbent is “off line” and not being utilized. This time spent regenerating may be kept as short as possible.
  • In accordance with some embodiments of the present disclosure, there is an adsorption-regeneration cycle that is incomplete, limited or interrupted by design. The phases are switched from adsorption to regeneration before the adsorbent is saturated, and the regeneration process may be stopped well before all the pollutants are released. This is done in order to achieve the best economics for indoor air scrubbing.
  • In some embodiments, the air treatment assembly 102 or scrubber may be configured to cycle between scrubbing at least one pollutant and/or gas from the stream of gases with the pollutant, and regenerating at least some of the adsorbent. The adsorption-regeneration cycle may comprise an adsorption phase which may be followed by a regeneration phase.
  • A complete adsorption phase may comprise a first time period for substantially saturating the adsorbent during the adsorption phase under the adsorption flow and temperature conditions being used. Similarly, a complete regeneration phase may comprise a second time period for removing substantially all of the removable pollutants and/or first gas from the adsorbent during the regeneration phase, under the purge flow and temperature conditions being used.
  • In accordance with some embodiments of the present disclosure, the duration of the second time period may be limited to a period of time which is less than the complete regeneration phase. Additionally or alternatively, the duration of the first time period may be limited to a period of time which is less than the complete adsorption phase.
  • In some embodiments the adsorption-regeneration cycle may comprise an adsorption phase followed by an optional first switchover time period, which may be followed by a regeneration phase. The regeneration phase may be followed by an optional second switchover time period.
  • In some embodiments, during the first switchover time period the adsorbent may be heated or may be maintained at the same temperature. In some embodiments, during the second switchover time period the adsorbent may be cooled down. The cool down may be facilitated by flowing unheated air through the sorbent during this time.
  • In accordance with some embodiments, the first switchover time period may comprises a period of time to bring the adsorbent to a temperature to release the pollutant from the adsorbent during the regeneration phase. The second switchover time period may comprise a period of time to bring the adsorbent to a temperature to adsorb the pollutant during the adsorption phase.
  • In a non-limiting example, the first time period may comprise about 95% of a complete adsorption phase. In some embodiments, the first time period may comprise about 90% of a complete adsorption phase. In some embodiments, the first time period may comprise about 80% of a complete adsorption phase. In some embodiments, the first time period may comprise about 50% of a complete adsorption phase. In some embodiments, the first time period may comprise about 20% of a complete adsorption phase. In some embodiments, the first time period may comprise about 20%-95% of a complete adsorption phase.
  • In a non-limiting example the second time period may comprise about 95% of a complete regeneration phase. In some embodiments, the second time period may comprise about 90% of a complete regeneration phase. In some embodiments, the second time period may comprise about 80% of a complete regeneration phase. In some embodiments, the second time period may comprise about 50% of a complete regeneration phase. In some embodiments, the second time period may comprise about 20% of a complete regeneration phase. In some embodiments, the second time period may comprise about 20%-95% of a complete regeneration phase.
  • Determining the duration of the limited period of time for the regeneration phase and/or the adsorption phase may be performed in any suitable manner, such as empirically via experimentation, for example.
  • In some embodiments, determining the duration of the limited period may be performed by a computer including a processor and a non-transitory machine-readable medium (for example).
  • In some embodiments, controlling cycling between the adsorption and regeneration phases may be performed by a computer including a processor and a non-transitory machine-readable medium, storing instructions having computer instructions operating thereon (for example).
  • In some embodiments, optimizing the cycle length and regeneration time may be performed by a system for controlling the air treatment assembly 102 (which may be referred to as the scrubber). The air treatment assembly 102 containing the adsorbent may be configured to cycle between scrubbing the pollutant and/or gas from the stream of gases in the incoming air and/or gas being adsorbed onto the adsorbent, and purging the pollutant and/or first gas from the adsorbent, via the regeneration gas flow. The air treatment assembly 102 may include means for flowing the stream of gases through the air treatment assembly 102 and over and/or through the adsorbent, where the adsorbent adsorbs the pollutant and/or gas from the stream of gases during the adsorption phase over a first time period. The air treatment assembly 102 may include means for flowing the regeneration gas flow over the adsorbent for purging a portion of the pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow. The air treatment assembly 102 may include means for cycling between the adsorption phase and the regeneration phase, where one cycle may comprise one adsorption phase followed by one regeneration phase. One cycle period may comprise the total time elapsed during a complete cycle or summation of the first time period, and the second time period. A complete regeneration phase may comprise a time period for removing substantially all of the pollutant and/or gas that can be removed from the adsorbent during the regeneration phase. A complete adsorption phase may comprise a time period for substantially saturating all the adsorbent during the adsorption. The duration of at least one of the following may be limited: the first time period to a period of time which is less than the complete adsorption phase and the second time period to a period of time which is less than the complete regeneration phase.
  • In some embodiments, the means for cycling may comprise a processor and a non-transitory machine-readable medium storing instructions having computer instructions operating thereon for controlling cycling between the adsorption and regeneration phases (for example).
  • In some embodiments, the means for cycling may comprise a control unit (not shown), such as an automated electromechanical control unit that determines when to open or close the dampers shown in FIG. 3 , for example, when to activate fans of FIG. 3 , for example, and may be responsible for flowing the incoming air purge gas through the system, for example. The air management system 100 of FIGS. 1A-1C and air management system 200 of FIGS. 2A-2B may also operate with sensors and actuators or any other suitable elements configured for determining when to activate the cycling means.
  • As described in reference to FIGS. 1A-3 , the means for flowing the stream of gases through the scrubber and the means for flowing the regeneration gas flow may comprise any suitable means. For example, the means may comprise dampers, fans, (such as shown in FIG. 3 ), valves, and/or shutters and ducts, inlets and outlets (such as shown in FIGS. 1A-3 ) and/or conduits.
  • In accordance with some embodiments the following analysis may be performed for determining the duration of the limited time period. The analysis is described in reference to a pollutant comprising CO2, but is applicable to any other pollutants.
  • A general rationale for incomplete regeneration is as follows: If the rate of release of CO2 slows down to a trickle, the adsorbent is nearing its clean state and can already be put to work effectively, so just like there is no reason to let the adsorbent idle, there is no reason to spend too much time regenerating it to the last few percent of capacity. The question is, what is the right time to stop regeneration and to switch back to adsorption.
  • For a given set of regeneration conditions, the rate of release of CO2 is denoted by R(t), measured in units of mass per time (such as moles per minute, grams per second, etc.), where t denotes the time measured from the beginning of the regeneration cycle. Typically R(t) increases at the beginning of the regeneration cycle as the adsorbent is heated while it is still loaded with CO2 but soon thereafter starts declining over time, as the amount of captured CO2 declines during the regeneration cycle, and thus, R(t) gradually trails off over an extended period.
  • On the adsorption side there is an analogous situation where A(t) is the rate at which CO2 is removed from the air flow, again measured in units of mass per time, and in analogy to R(t), it generally decreases as a function of time.
  • The typical cycle would have the adsorption phase continue for a time period of ta and then have the regeneration phase continue for a period tr. Since the amounts of carbon adsorbed and released have to balance each other in repeated cycles over the long run, it may be that the total amount adsorbed in a single adsorption phase, C, equals the amount released in a single regeneration phase, namely:
  • 0 t a A t d t = 0 t r R t d t = C
  • The length of the entire adsorption-regeneration cycle, T, is given by
  • T = t a + t r + t s
  • where ts is the optional switchover or pause time between adsorption phase and regeneration phase; for example, time allowed for the adsorbent to cool down or warm up as needed.
  • Since the amount of CO2 removed from the indoor air in each such cycle is C, the overall system productivity, p - defined as the average amount of CO2 removed per unit time - is simply
  • p = C T
  • But the value of p depends not only on the adsorbent and the environment in which it operates but also on our choice of ta and tr.
  • According to an embodiment, the optimal choice of tr, for any particular set of conditions in terms of temperature, flow rates and CO2 concentrations, may be approximately identified. In plugging equations (2) and (1) into (3) the following is received:
  • p = C T = 0 t r R t d t t a + t r + t s
  • Through basic calculus, the maximum value forp is obtained by taking its derivative with respect to tr and equating it to zero, namely
  • d p d t r = 0
  • Which can be expanded using basic derivative rules that state generally
  • d d x f g = g d x d f f d x d g g 2
  • So equation (5) requires
  • d d t r C T = d C d t r T d T d t r C T 2 = 0
  • Which implies that
  • d C d t r T d T d t r C = 0
  • Or in other words
  • d C d t r C = d T d t r T
  • This condition, although not an immediately solvable equation, is an important insight for the optimal design of indoor air adsorbent scrubbers, such as for single adsorbents or for more than one adsorbent designs . It can be further reduced to practice using the fact that, by definition,
  • d C d t r = R t r
  • And assuming ts is independent of tr,
  • d T d t r = 1 + d t a d t r
  • The following condition for tr is received
  • R t r = 1 + d t a d t r × p = β p
  • Where a new parameter, β, is introduced and may be simply defined as
  • β 1 + d t a d t r
  • Admittedly equation (12) is still not an explicit closed form expression that allows calculation of tr, but it is a useful design condition, and it does immediately suggest a lower bound, since β is always greater than 1. That means that at a minimum, it may be economically preferable to stop regeneration before the instantaneous rate R(t) drops below p, namely the following condition should be maintained
  • R t r p
  • It is a more reasonable estimate that
  • d t s d t r ~ 1
  • So it can be better approximated that β ≈ 2, thus having an even earlier threshold for stopping regeneration at
  • R t r ~ 2 p
  • Technically it remains an open equation because the value of p is not fixed, but it can be solved by iterations. This is a useful and practical guideline especially since the value of p varies relatively slowly with changes in tr so a few iterations will quickly converge on a very good approximation.
  • In some embodiments, empirically a more precise value for β can be derived, which would help refine formula (16), this may be performed by measuring the rate of adsorption towards the end of the cycle and comparing it to the rate of desorption. Two extremes are worth elaborating further.
  • In the case of classical “breakthrough”, the adsorption rate dramatically falls at the end of the cycle which means dtα >> dtr and β >>1, which translates into such a high threshold for R that regeneration may be stopped. In other words there may be no point or benefit in extending the regeneration phase if doing so does only causes lingering in adsorption mode post-breakthrough.
  • When there is only a very gradual decline in A(t) towards the end of the cycle, the opposite holds, namely dta < dtr and β ≈1, which means equation (14) is a good design criterion for timing the duration of the regeneration step.
  • It is noted that the principles described in this disclosure apply to a wide variety of scrubbing applications and CO2 or other pollutants removal applications using adsorbents in an adsorption-release cycle, and are not limited to indoor air applications.
  • As described above, in some embodiments, the regeneration phase may be terminated upon the regeneration rate R(tr) of the adsorbent being between about equal to and a predetermined amount less than the productivity p of the complete regeneration phase, where productivity
  • p = C T ,
  • and C equals an amount of the pollutant and/or first gas adsorbed by the adsorbent from the stream of gases during one cycle and T is the duration of one cycle period. This predetermined amount less than the productivity may be any suitable amount. In a non-limiting example, the predetermined amount may be in the range of 20-98% of the productivity p of the complete regeneration phase.
  • In some embodiments, the regeneration phase is terminated upon a regeneration rate R(tr) being between about equal to and about twice a productivity p of the complete regeneration phase, where productivity
  • p = C T ,
  • and C equals an amount of the pollutant and/or first gas adsorbed by the adsorbent from the stream of gases during one cycle and T is the duration of one cycle period.
  • In accordance with some embodiments there is described a method for removing a gas component including at least one adsorbate (which may also be referred to herein as a pollutant(s) and/or a particular gas(s)) from a stream of mixed gases, the method may comprise one or more of: using an adsorbent material in a repeated cyclical fashion, with at least two distinct phases in each cycle, one being an adsorption phase where the adsorbate is partially removed from the streaming gas mixture onto the adsorbent, and one being a regeneration phase where the adsorbate is released from the adsorbent and carried away. The duration of the regeneration phase may be substantially shorter than a complete regeneration phase, the complete regeneration phase being the time to release substantially all of the adsorbate that can be released under the temperature and flow conditions of the system.
  • In accordance with some embodiments at least an additional 10% of the adsorbate could be released if the regeneration phase were extended by 100%. Alternatively, at least an additional 5% of the adsorbate could be released if the regeneration phase were extended by 100%.
  • The example set forth herein is meant to exemplify various aspects of the disclosure and is not intended to limit in any way.
  • EXAMPLE
  • Reference is made to FIG. 4 , which is a graph showing a method for calculating the optimal adsorption-regeneration cycle and in accordance with the formulas described hereinabove. As seen in FIG. 4 the values of the following parameters are substantially:
    • ta= 53 min
    • ts= 5 min
    • tr= 34 min
  • Thus, T is the sum of ta+ ts + tr = 92 min
  • C=70 grams
  • Therefore
  • p = C T = 70 / 92 = 0.76
  • [grams per minutes]
  • Thus, the regeneration may be stopped where R(tr) according to formula (14) is equal or larger than 0.76 (grams per minutes) or according to formula (16) where R(tr) is substantially equal to 1.52 (grams per minutes).
  • In accordance with some embodiments prior to streaming the regeneration air flow in the reverse direction to the incoming air, as described in reference to FIGS. 1A-3 , or in the same direction, the following may be determined: the amount of the pollutant in the scrubbed air flow and/or the ability of the adsorbent to capture an additional amount of the pollutant over and above a predetermined amount, and when the amount of the pollutant is greater than a predetermined amount, and/or the adsorbent has captured the predetermined amount of the pollutant, streaming of the regeneration air flow over and/or through the adsorbent is performed.
  • The amount of the pollutant in the scrubbed air flow and/or the ability of the adsorbent to capture an additional amount of the at least one pollutant may be determined in any suitable manner, such as by a computer including a processor and a non-transitory machine-readable medium (for example).
  • This predetermined amount of the pollutant may be any suitable amount. In a non-limiting example, the predetermined amount may be an amount of the pollutant that substantially saturates the adsorbent. In a non-limiting example, the predetermined amount may be less than the amount of the pollutant that substantially saturates the adsorbent.
  • In accordance with some embodiments prior to streaming the regeneration air flow in the reverse direction to the incoming air, as described in reference to FIGS. 1A-3 , or in the same direction, the following may be determined: a level of an adsorption efficiency, where the adsorption efficiency at any point in time during the one cycle has a value of 1 - Cin/Cout. Cin is the concentration of the pollutant in the incoming air flow and Cout is the concentration of the pollutant in the outgoing air flow. When the adsorption efficiency value is less than an initial adsorption efficiency value, streaming of the regeneration air flow over and/or through the adsorbent is performed. The initial adsorption efficiency value is the adsorption efficiency value at the beginning of the adsorption phase.
  • The adsorption efficiency value and the initial adsorption efficiency value may be determined in any suitable manner, such as by a computer including a processor and a non-transitory machine-readable medium (for example).
  • In some embodiments, where the adsorption efficiency value is less than the initial adsorption efficiency value, a regeneration air flow is streamed through the air treatment assembly 102 and over and/or through the adsorbent in a second direction opposite to the first direction of the incoming air, such that the regeneration air flow regenerates at least some of the adsorbent and purges at least some of the pollutants from the adsorbent.
  • In some embodiments, streaming of the regeneration air flow over and/or through the adsorbent is performed where the adsorption efficiency value is at least about 20% less than the initial adsorption efficiency value. In some embodiments, streaming of the regeneration air flow over and/or through the adsorbent is performed where the adsorption efficiency value is at least about 30% less than the initial adsorption efficiency value. In some embodiments, streaming of the regeneration air flow over and/or through the adsorbent is performed where the adsorption efficiency value is at least about 50% less than the initial adsorption efficiency value. In some embodiments, streaming of the regeneration air flow over and/or through the adsorbent is performed where the adsorption efficiency value is at least about 80% less than the initial adsorption efficiency value.
  • In is noted that the air treatment assembly 102 described above in reference to FIGS. 1A-4 , may be configured to treat any stream of gas, such as air from the enclosed environment 110, flue gases, or nitrogen with elevated levels of carbon dioxide, organic contaminants relative to substantially unpolluted air, or outside air.
  • Various implementations of some of embodiments disclosed, in particular at least some of the processes discussed (or portions thereof), may be realized in digital electronic circuitry, integrated circuitry, specially designed ASICs (application specific integrated circuits), computer hardware, firmware, software, and/or combinations thereof. These various implementations may include implementation in one or more computer programs that are executable and/or interpretable on a programmable system including at least one programmable processor, which may be special or general purpose, coupled to receive data and instructions from, and to transmit data and instructions to, a storage system, at least one input device, and at least one output device.
  • Such computer programs (also known as programs, software, software applications or code) include machine instructions/code for a programmable processor, for example, and may be implemented in a high-level procedural and/or object-oriented programming language, and/or in assembly/machine language. As used herein, the term “machine-readable medium” refers to any computer program product, apparatus and/or device (e.g., non-transitory mediums including, for example, magnetic discs, optical disks, flash memory, Programmable Logic Devices (PLDs)) used to provide machine instructions and/or data to a programmable processor, including a machine-readable medium that receives machine instructions as a machine-readable signal. The term “machine-readable signal” refers to any signal used to provide machine instructions and/or data to a programmable processor.
  • To provide for interaction with a user, the subject matter described herein may be implemented on a computer having a display device (e.g., a CRT (cathode ray tube) or LCD (liquid crystal display) monitor and the like) for displaying information to the user and a keyboard and/or a pointing device (e.g., a mouse or a trackball, touchscreen) by which the user may provide input to the computer. For example, this program can be stored, executed and operated by the dispensing unit, remote control, PC, laptop, smart-phone, media player or personal data assistant (“PDA”). Other kinds of devices may be used to provide for interaction with a user as well. For example, feedback provided to the user may be any form of sensory feedback (e.g., visual feedback, auditory feedback, or tactile feedback), and input from the user may be received in any form, including acoustic, speech, or tactile input.
  • Certain embodiments of the subject matter described herein may be implemented in a computing system and/or devices that includes a back-end component (e.g., as a data server), or that includes a middleware component (e.g., an application server), or that includes a front-end component (e.g., a client computer having a graphical user interface or a Web browser through which a user may interact with an implementation of the subject matter described herein), or any combination of such back-end, middleware, or front-end components. The components of the system may be interconnected by any form or medium of digital data communication (e.g., a communication network). Examples of communication networks include a local area network (“LAN”), a wide area network (“WAN”), and the Internet.
  • The computing system according to some such embodiments described above may include clients and servers. A client and server are generally remote from each other and typically interact through a communication network. The relationship of client and server arises by virtue of computer programs running on the respective computers and having a client-server relationship to each other.
  • Any and all references to publications or other documents, including but not limited to, patents, patent applications, articles, webpages, books, etc., presented anywhere in the present application, are herein incorporated by reference in their entirety.
  • Example embodiments of the devices, systems and methods have been described herein. As may be noted elsewhere, these embodiments have been described for illustrative purposes only and are not limiting. Other embodiments are possible and are covered by the disclosure, which will be apparent from the teachings contained herein. Thus, the breadth and scope of the disclosure should not be limited by any of the above-described embodiments but should be defined only in accordance with claims supported by the present disclosure and their equivalents. Moreover, embodiments of the subject disclosure may include methods, systems and devices which may further include any and all elements/features from any other disclosed methods, systems, and devices, including any and all features corresponding to translocation control. In other words, features from one and/or another disclosed embodiment may be interchangeable with features from other disclosed embodiments, which, in turn, correspond to yet other embodiments. Furthermore, one or more features/elements of disclosed embodiments may be removed and still result in patentable subject matter (and thus, resulting in yet more embodiments of the subject disclosure).

Claims (44)

What is claimed is:
1. A method for controlling a scrubber containing an adsorbent, the scrubber configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the at least one pollutant and/or first gas being adsorbed onto the adsorbent, and regenerating at least some of the adsorbent and thereby purging at least some of the at least one pollutant and/or first gas from the adsorbent via a regeneration gas flow, the method comprising:
flowing a stream of gases through the scrubber, the scrubber comprising the adsorbent;
adsorbing at least some of the one pollutant and/or first gas from the stream of gases onto the adsorbent during an adsorption phase over a first time period;
purging a portion of the at least one pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and
cycling between the adsorption phase and the regeneration phase, wherein
one cycle comprises at least an adsorption phase followed by a regeneration phase,
one cycle period comprises the total time elapsed during one cycle,
the at least one pollutant and/or first gas purged from the adsorbent is carried away by the regeneration gas flow, and
a complete regeneration phase comprises a time period for removing substantially all of the pollutant and/or first gas from the adsorbent during the regeneration phase, and
a complete adsorption phase comprises a time period for substantially saturating all the adsorbent during the adsorption; and
limiting at least one of:
the duration of the first time period to a period of time which is less than the complete adsorption phase, and
the duration of the second time period to a period of time which is less than the complete regeneration phase.
2. The method of claim 1, wherein the first time period comprises about 95% of a complete adsorption phase.
3. The method of claim 1, wherein the first time period is about 90% of a complete adsorption phase.
4. The method of claim 1, wherein the first time period is about 80% of a complete adsorption phase.
5. The method of claim 1, wherein the first time period is about 50% of a complete adsorption phase.
6. The method of claim 1, wherein the first time period is about 20% of a complete adsorption phase.
7. The method of claim 1, wherein the first time period comprises about 20% to about 95% of a complete adsorption phase.
8. The method of claim 1, wherein the second time period comprises about 95% of a complete regeneration phase.
9. The method of claim 1, wherein the second time period is about 90% of a complete regeneration phase.
10. The method of claim 1, wherein the second time period is about 80% of a complete regeneration phase.
11. The method of claim 1, wherein the second time period is about 50% of a complete regeneration phase.
12. The method of claim 1, wherein the second time period is about 20% of a complete regeneration phase.
13. The method of claim 1, wherein the second time period comprises about 20% to about 95% of a complete regeneration phase.
14. The method of claim 1, wherein:
the regeneration phase is terminated upon a regeneration rate R(tr) of the adsorbent being between about equal to and a predetermined amount less than a productivity p of the complete regeneration phase, wherein
productivity
p = C T ,
and
C equals an amount of the pollutant and/or first gas adsorbed by the adsorbent from the stream of gases during one cycle and T is the duration of one cycle period.
15. The method of claim 1, wherein:
the regeneration phase is terminated upon a regeneration rate R(tr) being between about equal to and about twice a productivity p of the complete regeneration phase, wherein
productivity
p = C T ,
and
C equals an amount of the pollutant and/or first gas adsorbed by the adsorbent from the stream of gases during one cycle and T is the duration of one cycle period.
16. The method of claim 1, wherein the pollutant and/or first gas is selected from the group consisting of: carbon dioxide, volatile organic compounds, sulfur oxides, radon, nitrous oxides and carbon monoxide.
17. The method of claim 1, wherein the adsorbent comprises at least one of : an amine supported by a solid, activated carbon, clay, carbon fibers, silica, alumina, zeolites, molecular sieves, titanium oxide, polymer, porous polymers, polymer fibers and metal organic frameworks.
18. The method of claim 17, wherein the supporting solid is at least one of silica, carbon, clay or metal oxide.
19. The method of claim 1, wherein the adsorbent comprises granular solids or pelleted shaped solids.
20. The method of claim 1, wherein the stream of gases comprises air from an enclosed environment, outdoor air, flue gases, or nitrogen with elevated levels of carbon dioxide or organic contaminants, relative to substantially unpolluted air.
21. The method of claim 1 wherein the one cycle may further comprise at least one of :
(i) a first switchover phase prior to the regeneration phase, and (ii) a second switchover phase following the regeneration phase.
22. The method of claim 21, wherein the second switchover phase comprises a period of time to bring the adsorbent to a temperature to adsorb the at least one pollutant and/or first gas during the adsorption phase.
23. The method of claim 21, wherein the first switchover phase comprises a period of time to bring the adsorbent to a temperature to release the at least one pollutant and/or first gas from the adsorbent during the regeneration phase.
24. The method of claim 1, wherein prior to streaming the regeneration gas flow the method further includes determining a level of an adsorption efficiency, wherein the adsorption efficiency at any point in time during the one cycle has a value of 1 - Cin/Cout, wherein Cin is the concentration of the pollutant in the incoming air flow and Cout is the concentration of the pollutant in an outgoing air flow, and wherein an initial adsorption efficiency value is the adsorption efficiency value at the beginning of the adsorption phase,
wherein the adsorption efficiency value is less than the initial adsorption efficiency value, streaming of the regeneration gas flow over and/or through the adsorbent is performed.
25. A system for controlling a scrubber, the system comprising:
a scrubber containing an adsorbent, the scrubber configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the at least one pollutant and/or first gas being adsorbed onto the adsorbent, and purging the at least one pollutant and/or first gas from the adsorbent via a regeneration gas flow;
means for flowing the stream of gases through the scrubber and over and/or through the adsorbent, wherein the adsorbent adsorbs at least one pollutant and/or first gas from the stream of gases during an adsorption phase over a first time period;
means for flowing the regeneration gas flow over the adsorbent for purging a portion of the pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and
means for cycling between the adsorption phase and the regeneration phase, wherein
one cycle comprises one adsorption phase followed by one regeneration phase,
one cycle period comprises the total time elapsed during one cycle;
the pollutant and/or first gas purged from the adsorbent is carried away by the regeneration gas flow,
a complete regeneration phase comprises a time period for removing substantially all of the pollutant and/or first gas from the adsorbent during the regeneration phase,
a complete adsorption phase comprises a time period for substantially saturating all the adsorbent during the adsorption, and
the duration of at least one of the following is limited:
the duration of the first time period to a period of time which is less than the complete adsorption phase, and
the duration of the second time period to a period of time which is less than the complete regeneration phase.
26. The system of claim 25, wherein the means for cycling comprises a processor and a non-transitory machine-readable medium storing instructions having computer instructions operating thereon for controlling cycling between the adsorption and regeneration phases.
27. A computer implemented method for controlling a scrubber containing an adsorbent, the scrubber configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the at least one pollutant and/or first gas being adsorbed onto the adsorbent, and purging the at least one pollutant and/or first gas from the adsorbent via a purging gas flow, the method comprising:
flowing a stream of gases through the scrubber, the scrubber comprising an adsorbent;
adsorbing at least one pollutant and/or first gas from the stream of gases onto the adsorbent during an adsorption phase over a first time period,
purging a portion of the at least one pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and
cycling between the adsorption phase and the regeneration phase, wherein
one cycle comprises one adsorption phase followed by one regeneration phase,
one cycle period comprises the total time elapsed during one cycle;
the at least one pollutant and/or first gas purged from the adsorbent is carried away by the regeneration gas flow, and
a complete regeneration phase comprises a time period for removing substantially all of the pollutant and/or first gas from the adsorbent during the regeneration phase,
a complete adsorption phase comprises a time period for substantially saturating all the adsorbent during the adsorption; and
limiting at least one of:
the duration of the first time period to a period of time which is less than the complete adsorption phase, and
the duration of the second time period to a period of time which is less than the complete regeneration phase,
wherein at least one of the above is performed by at least one processor.
28. A system for controlling a scrubber containing an adsorbent, the scrubber configured to cycle between scrubbing at least one pollutant and/or first gas from a stream of gases with the at least one pollutant and/or first gas being adsorbed onto the adsorbent, and purging the at least one pollutant and/or first gas from the adsorbent via a regeneration gas flow, the system comprising at least one processor and a non-transitory machine-readable medium storing instructions that, when executed by the at least one processor, perform the method comprising:
flowing a stream of gases over and/or through the adsorbent, wherein the adsorbent adsorbs at least some of the at least one pollutant and/or first gas from the stream of gases during an adsorption phase over a first time period;
purging a portion of the at least one pollutant and/or first gas from the adsorbent during a regeneration phase over a second time period with a regeneration gas flow, and
cycling between the adsorption phase and the regeneration phase, wherein
one cycle comprises one adsorption phase followed by one regeneration phase,
one cycle period comprises the total time elapsed during one cycle,
the at least one pollutant and/or first gas being purged from the adsorbent is carried away by the regeneration gas flow, and
a complete regeneration phase comprises a time period for removing substantially all of the at least one pollutant and/or first gas from the adsorbent during the regeneration phase,
a complete adsorption phase comprises a time period for substantially saturating all the adsorbent during the adsorption, and
limiting at least one of:
the duration of the first time period to a period of time which is less than the complete adsorption phase, and
the duration of the second time period to a period of time which is less than the complete regeneration phase.
29. A method for reducing the level of at least one pollutant contained in indoor air from a human-occupied, enclosed environment, the method comprising:
providing an air treatment assembly including at least one type of adsorbent, the adsorbent configured for capturing at least one pollutant entrained in an indoor air flow from the enclosed environment and regenerating upon exposure to a regenerating gas flow;
streaming the indoor air flow over and/or through the adsorbent in a first direction such that the adsorbent captures at least some of the at least one pollutant from the indoor air flow, wherein after being flowed over and/or through the adsorbent, the air flow comprises a scrubbed air flow; and
streaming the regeneration gas flow over and/or through the adsorbent in a second direction opposite to the first direction, such that the regeneration gas flow regenerates at least some of the adsorbent and purges at least some of the at least one pollutant from the adsorbent.
30. The method of claim 29 where there are at least two adsorbents such that the streaming indoor air flows through a first adsorbent and subsequently through a second adsorbent, and that as a result of the reversal of the flow direction during regeneration, substances purged from the first adsorbent do not flow across the second adsorbent.
31. The method of claim 29 where pollutants are released from the adsorbent during regeneration and may accumulate in the air treatment assembly or air conduits attached to it, and as a result of the reversal of the flow direction during regeneration, the released pollutants are substantially prevented from accumulating downstream from the adsorbent and accumulate substantially in sections of the air treatment assembly that are upstream from the adsorbent,
the air treatment assembly comprising an inlet for indoor air flowing through the adsorbent; and
upstream the adsorbent being in greater proximity to the inlet than downstream the adsorbent.
32. The method of claim 29, wherein the pollutant and/or first gas is selected from the group consisting of: carbon dioxide, volatile organic compounds, sulfur oxides, radon, nitrous oxides and carbon monoxide.
33. The method of claim 29, wherein the adsorbent comprises at least one of an amine supported by a solid, activated carbon, clay, carbon fibers, silica, alumina, zeolites, molecular sieves, titanium oxide, polymer, porous polymers, polymer fibers and metal organic framework.
34. The method of claim 33, wherein the supporting solid is at least one of silica, carbon, clay or metal oxide.
35. The method of claim 29, wherein the adsorbent comprises granular solids or pelleted shaped solids.
36. A computer implemented method for reducing the level of at least one pollutant contained in indoor air from an enclosed, human-occupied environment, the method comprising:
streaming an indoor air flow over and/or through an adsorbent provided within an air treatment assembly in a first direction, the indoor air flow containing at least one pollutant from inside the enclosed environment, such that the adsorbent captures at least some of the at least one pollutant from the indoor air, wherein after being flowed over and/or through the adsorbent, the air flow comprises a scrubbed air flow;
determining a level of an adsorption efficiency, wherein the adsorption efficiency at any point in time during the one cycle has a value of 1 - CinCout, wherein Cin is the concentration of the pollutant in the incoming air flow and Cout is the concentration of the pollutant in an outgoing air flow, and wherein an initial adsorption efficiency value is the adsorption efficiency value at the beginning of the adsorption phase,
wherein the adsorption efficiency value is less than the initial adsorption efficiency value, and
streaming a regeneration air flow through the air treatment assembly and over and/or through the adsorbent in a second direction opposite to the first direction, such that the regeneration air flow regenerates at least some of the adsorbent and purges at least some of the at least one pollutant from the adsorbent,
wherein at least one of the above is performed by a processor.
37. A system for reducing the level of at least one pollutant contained in indoor air from an enclosed, human-occupied environment, the method comprising:
an air treatment assembly including an adsorbent, the adsorbent configured for capturing at least one pollutant entrained in an indoor air flow and regenerating upon exposure to a regenerating gas flow; and
streaming means for:
streaming the indoor air flow over and/or through the adsorbent in a first direction, such that the adsorbent captures at least some of the at least one pollutant from the indoor air flow, and
streaming the regeneration air flow over and/or through the adsorbent in a second direction opposite to the first direction, such that the regeneration gas flow regenerates at least some of the adsorbent and purges at least some of the at least one pollutant from the adsorbent.
38. A system for reducing the level of at least one pollutant contained in indoor air from an enclosed, human-occupied environment, the system comprising:
an air treatment assembly including an adsorbent, the adsorbent configured for capturing at least one pollutant entrained in an indoor air flow and regenerating upon exposure to a regenerating gas flow;
streaming means for streaming the indoor air flow over and/or through the adsorbent in a first direction, and/or for streaming the regeneration gas flow over and/or through the adsorbent in a second direction opposite to the first direction;
at least one processor;
a non-transitory machine-readable medium storing instructions that, when executed by the at least one processor, perform the method comprising:
streaming the indoor air over and/or through the adsorbent in the first direction such that the adsorbent captures at least some of the at least one pollutant from the indoor air; and
determining a level of an adsorption efficiency, wherein the adsorption efficiency at any point in time during the one cycle has a value of 1 - Cin/Cout, wherein Cin is the concentration of the pollutant in the incoming air flow and Cout is the concentration of the pollutant in an outgoing air flow, and wherein an initial adsorption efficiency value is the adsorption efficiency value at the beginning of the adsorption phase, wherein the adsorption efficiency value is less than the initial adsorption efficiency value, streaming of the regeneration gas flow over and/or through the adsorbent is performed.
39. A method for reducing the level of at least one pollutant contained in indoor air from an enclosed, human-occupied environment, the method comprising:
providing an air treatment assembly including an adsorbent, the adsorbent configured for capturing at least one pollutant entrained in an indoor air flow from the enclosed environment and regenerating upon exposure to a regenerating gas flow;
streaming the indoor air flow over and/or through the adsorbent in a first direction such that the adsorbent captures at least some of the at least one pollutant from the indoor air flow, wherein the streaming of the indoor air flow over and/or through the adsorbent comprises an adsorption phase; and
streaming the regeneration gas flow over and/or through the adsorbent in a second direction opposite to the first direction, such that the regeneration air flow regenerates at least some of the adsorbent and purges at least some of the at least one pollutant from the adsorbent, wherein the streaming of the regeneration gas flow over and/or through the adsorbent comprises a regeneration phase,
cycling between the adsorption phase and the regeneration phase, wherein
one cycle comprises an adsorption phase followed by a regeneration phase,
one cycle period comprises the total time elapsed during one cycle;
the at least one pollutant purged from the adsorbent is carried away by the regeneration gas flow, and
a complete regeneration phase comprises a time period for removing substantially all of the at least one pollutant from the adsorbent during the regeneration phase, and and
a complete adsorption phase comprises a time period for substantially saturating all the adsorbent during the adsorption; and
limiting at least one of:
the duration of the first time period to a period of time which is less than the complete adsorption phase, and
the duration of the second time period to a period of time which is less than the complete regeneration phase.
40. The method of claim 39, wherein prior to streaming the regeneration gas flow the method further includes determining a level of an adsorption efficiency, wherein the adsorption efficiency at any point in time during the one cycle has a value of 1 - Cin/Cout, wherein Cin is the concentration of the pollutant in the incoming air flow and Cout is the concentration of the pollutant in an outgoing air flow, and wherein an initial adsorption efficiency value is the adsorption efficiency value at the beginning of the adsorption phase, wherein the adsorption efficiency value is less than the initial adsorption efficiency value, streaming of the regeneration gas flow over and/or through the adsorbent is performed.
41. The method of claim 40 wherein the adsorption efficiency value is at least about 20% less than the initial adsorption efficiency value.
42. The method of claim 40 wherein the adsorption efficiency value is at least about 30% less than the initial adsorption efficiency value.
43. The method of claim 40 wherein the adsorption efficiency value is at least about 50% less than the initial adsorption efficiency value.
44. The method of claim 40 wherein the adsorption efficiency value is at least about 80% less than the initial adsorption efficiency value.
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US11890571B2 (en) 2012-11-15 2024-02-06 Enverid Systems, Inc. Method and system for reduction of unwanted gases in indoor air

Families Citing this family (26)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8157892B2 (en) 2010-05-17 2012-04-17 Enverid Systems, Inc. Method and system for improved-efficiency air-conditioning
WO2013177290A2 (en) * 2012-05-22 2013-11-28 Enverid Systems, Inc. Efficient use of adsorbents for indoor air scrubbing
US9950290B2 (en) 2012-07-18 2018-04-24 Enverid Systems, Inc. Systems and methods for regenerating adsorbents for indoor air scrubbing
CN104685300B (en) 2012-09-24 2017-11-28 恩沃德系统公司 Air treatment system with integration air processing
WO2015042150A1 (en) 2013-09-17 2015-03-26 Enverid Systems, Inc. Systems and methods for efficient heating of sorbents in an indoor air scrubber
KR20160094156A (en) * 2015-01-30 2016-08-09 서강대학교산학협력단 Device for exhausting carbon dioxide associated with heating or air-conditioning device
KR102640374B1 (en) 2015-03-23 2024-02-26 바스프 코포레이션 Carbon dioxide sorbent to control indoor air quality
WO2016183237A1 (en) 2015-05-11 2016-11-17 Enverid Systems, Inc. Method and system for reduction of unwanted gases in indoor air
US10792608B2 (en) 2015-08-24 2020-10-06 Enverid Systems, Inc. Scrubber for HVAC system
WO2017139555A1 (en) 2016-02-12 2017-08-17 Basf Corporation Carbon dioxide sorbents for air quality control
US11207633B2 (en) 2016-04-19 2021-12-28 Enverid Systems, Inc. Systems and methods for closed-loop heating and regeneration of sorbents
WO2017219043A1 (en) * 2016-06-17 2017-12-21 Enverid Systems, Inc. Apparatus, methods and systems for multi-stage scrubbing of gas mixtures
CN109952140A (en) 2016-11-10 2019-06-28 恩弗里德系统公司 The room air washer that low noise, ceiling are installed
JP6970522B2 (en) * 2017-04-27 2021-11-24 川崎重工業株式会社 Air purification system
JP6447770B2 (en) * 2017-06-02 2019-01-09 ダイキン工業株式会社 Ventilation system
US10830467B2 (en) 2017-06-21 2020-11-10 Air Distribution Technologies Ip, Llc HVAC scrubber unit operational control systems and methods
USD844650S1 (en) 2017-10-31 2019-04-02 Air Distribution Technologies Ip, Llc Electronic display with graphical user interface for an HVAC scrubber unit
CN108201773B (en) * 2017-12-19 2021-03-02 昆明理工大学 Method for absorbing volatile organic compounds in gas by using hydrophilic switchable reversible solvent
US11074899B2 (en) 2018-03-15 2021-07-27 International Business Machines Corporation VOC sequestering acoustic foam
SE543981C2 (en) * 2018-07-13 2021-10-12 Sally R Ab Module for treating air, method for treating air, and related systems
CN110871014A (en) * 2018-08-30 2020-03-10 开利公司 CO with moving bed structure2Washing device
US11376544B2 (en) 2018-11-07 2022-07-05 Air Distribution Technologies Ip, Llc Contaminant scrubber of a heating, ventilation, and air conditioning (HVAC) system
JP7203674B2 (en) * 2019-04-11 2023-01-13 日立造船株式会社 Exhaust gas treatment device and exhaust gas treatment method
US20230015857A1 (en) * 2020-01-21 2023-01-19 Top Product Innovations Method to reduce both vocs and co2 in living and working spaces
US11885510B2 (en) * 2020-09-16 2024-01-30 Johnson Controls Tyco IP Holdings LLP Systems and methods to mitigate infection risk using air purification
CN113433267B (en) * 2021-06-11 2023-12-15 青岛海尔空调器有限总公司 Air abnormality early warning method, device, equipment, medium and program product

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4816043A (en) * 1985-05-31 1989-03-28 Wilkerson Coporation Adsorption-desorption fluid fractionation with cycle phase switching controlled by purge and saturation front conditions
US8157892B2 (en) * 2010-05-17 2012-04-17 Enverid Systems, Inc. Method and system for improved-efficiency air-conditioning
US20120160099A1 (en) * 2009-07-27 2012-06-28 Kawasaki Jukogyo Kabushiki Kaisha Carbon dioxide separation method and apparatus
US9566545B2 (en) * 2012-05-22 2017-02-14 Enverid Systems, Inc. Efficient use of adsorbents for indoor air scrubbing

Family Cites Families (269)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US1522480A (en) 1921-03-03 1925-01-13 Henry L Doherty & Company Method of solvent recovery
US1836301A (en) 1926-05-31 1931-12-15 Bechthold Friedrich Jakob Regenerating granular adsorbents
US2633928A (en) 1946-09-28 1953-04-07 Chester A Chamberlain Dehumidifying apparatus
US3042497A (en) 1959-03-09 1962-07-03 Wayne W Johnson Co2 scrubber
US3107641A (en) 1961-03-03 1963-10-22 Jet Res Ct Inc Submarine vessel
US3344050A (en) 1964-02-03 1967-09-26 Girdler Corp Removal of carbon dioxide from gaseous atmospheres
US3511595A (en) 1967-05-18 1970-05-12 Treadwell Corp The Method of removing carbon dioxide and water vapor from air
US3619130A (en) 1968-08-27 1971-11-09 Frank J Ventriglio Method of removing carbon dioxide from gaseous mixtures
US3594983A (en) 1969-06-17 1971-07-27 Process Services Inc Gas-treating process and system
US3702049A (en) 1970-09-24 1972-11-07 Ewel J Morris Jr Device for cleaning polluted air
DE2064137B2 (en) 1970-12-28 1971-09-16 METHOD AND DEVICE FOR ADSORPTIVE REMOVAL OF WATER AND ONE OR MORE OTHER COMPONENTS FROM GASES
US3751848A (en) 1972-03-13 1973-08-14 R Ahlstrand Model house
US3795090A (en) 1972-08-25 1974-03-05 Barnebey Cheney Co Fluid filter construction
US3751878A (en) 1972-10-20 1973-08-14 Union Carbide Corp Bulk separation of carbon dioxide from natural gas
US3885928A (en) 1973-06-18 1975-05-27 Standard Oil Co Ohio Acrylonitrile and methacrylonitrile recovery and purification system
US3885927A (en) 1974-02-05 1975-05-27 Union Carbide Corp Process for removing carbon dioxide from gas streams
US4182743A (en) 1975-11-10 1980-01-08 Philip Morris Incorporated Filter material for selective removal of aldehydes for cigarette smoke
US4292059A (en) 1977-09-19 1981-09-29 Kovach Julius L By-pass proof adsorber cell
US4322394A (en) 1977-10-31 1982-03-30 Battelle Memorial Institute Adsorbent regeneration and gas separation utilizing microwave heating
US4228197A (en) 1979-01-18 1980-10-14 Food Storage Systems, Inc. Atmosphere controlling method and apparatus for food storage
US4238460A (en) 1979-02-02 1980-12-09 United States Steel Corporation Waste gas purification systems and methods
US4249915A (en) 1979-05-30 1981-02-10 Air Products And Chemicals, Inc. Removal of water and carbon dioxide from air
US4530817A (en) 1980-01-03 1985-07-23 Heinz Holter Apparatus for the protection of air fed to a labor-protection or vehicle compartment
JPS56158126A (en) 1980-05-12 1981-12-05 Taikisha Ltd Adsorber-desorber
EP0050243B1 (en) 1980-10-17 1991-12-11 Heinz Dipl.-Ing. Hölter Process and apparatus for cleaning air charged with noxious gases
US4551304A (en) 1980-10-17 1985-11-05 Heinz Holter Method of cleaning air loaded with pollutants
US4433981A (en) 1981-02-18 1984-02-28 Shell Oil Company CO2 Removal from gaseous streams
GB2109268B (en) 1981-11-16 1984-10-03 Process Scient Innovations Gas purifiers
US4409006A (en) 1981-12-07 1983-10-11 Mattia Manlio M Removal and concentration of organic vapors from gas streams
JPS59225232A (en) 1983-06-05 1984-12-18 Mitsuhiro Isono Space oxygenating device
US4472178A (en) 1983-07-05 1984-09-18 Air Products And Chemicals, Inc. Adsorptive process for the removal of carbon dioxide from a gas
JPS60194243A (en) 1984-03-14 1985-10-02 Nikka Micron Kk Indoor air conditioning and purifying method by sodium carbonate peroxide
CA1241524A (en) 1985-01-21 1988-09-06 Hyman D. Gesser Abatement of indoor formaldehyde vapour and other indoor gaseous pollutants
US4711645A (en) 1986-02-10 1987-12-08 Air Products And Chemicals, Inc. Removal of water and carbon dioxide from atmospheric air
US4764187A (en) 1987-02-09 1988-08-16 Rad Systems, Inc. Regenerating dynamic adsorber system and method for contaminant removal
US4810266A (en) 1988-02-25 1989-03-07 Allied-Signal Inc. Carbon dioxide removal using aminated carbon molecular sieves
US4917862A (en) 1988-04-15 1990-04-17 Allan Kraw Filter and method for removing mercury, bacteria, pathogens and other vapors from gas
JPH074433B2 (en) 1988-09-28 1995-01-25 東海興業株式会社 Indoor carbon dioxide abatement system for construction
US4863494A (en) 1988-10-31 1989-09-05 Hayes William V Air purification apparatus including high temperature regenerated adsorbent particles
JPH03207936A (en) 1989-03-29 1991-09-11 Toshimi Yoshida Oxygen generator and air-conditioning system
US4976749A (en) 1989-04-24 1990-12-11 Raytheon Company Air filter and particle removal system
JP3029841B2 (en) 1990-04-16 2000-04-10 株式会社豊田中央研究所 Composite adsorbent and method for producing the same
US4987952A (en) 1990-04-26 1991-01-29 Dumont Holding Company Apparatus for use in dehumidifying and otherwise conditioning air within a room
FR2661841B1 (en) 1990-05-09 1992-07-17 Air Liquide AIR ADSORPTION CLEANING PROCESS AND APPARATUS FOR DISTILLE.
US5322473A (en) 1990-05-17 1994-06-21 Quality Air Systems, Inc. Modular wall apparatus and method for its use
US5194158A (en) 1990-06-15 1993-03-16 Matson Stephen L Radon removal system and process
US5087597A (en) 1990-07-19 1992-02-11 Armada De La Republica De Venezuela Carbon dioxide adsorbent and method for producing the adsorbent
NL9001890A (en) 1990-08-29 1992-03-16 Jong C H De Bv SYSTEM FOR PURIFYING AIR.
US5046319A (en) 1990-10-16 1991-09-10 California Institute Of Technology Regenerative adsorbent heat pump
US5109916A (en) 1990-10-31 1992-05-05 Carrier Corporation Air conditioning filter system
US5149343A (en) 1991-02-22 1992-09-22 Sowinski Richard F Method for filtering radon from a gas stream
US5471852A (en) 1991-07-05 1995-12-05 Meckler; Milton Polymer enhanced glycol desiccant heat-pipe air dehumidifier preconditioning system
US5221520A (en) 1991-09-27 1993-06-22 North Carolina Center For Scientific Research, Inc. Apparatus for treating indoor air
US5186903A (en) 1991-09-27 1993-02-16 North Carolina Center For Scientific Research, Inc. Apparatus for treating indoor air
JPH05161843A (en) 1991-12-16 1993-06-29 Osaka Gas Co Ltd Carbon dioxide adsorbent
US5292280A (en) 1992-02-14 1994-03-08 Johnson Service Co. Method and apparatus for controlling ventilation rates and indoor air quality in an HVAC system
US5281254A (en) 1992-05-22 1994-01-25 United Technologies Corporation Continuous carbon dioxide and water removal system
JP3207936B2 (en) 1992-07-07 2001-09-10 日空工業株式会社 Method for carbonizing pitch-containing refractories
JP2659652B2 (en) 1992-07-14 1997-09-30 株式会社神戸製鋼所 Dry dehumidifier
CN2141873Y (en) 1992-11-07 1993-09-08 戚鸣 Indoor air purifier
US5376614A (en) 1992-12-11 1994-12-27 United Technologies Corporation Regenerable supported amine-polyol sorbent
US5290345A (en) 1993-01-13 1994-03-01 Donaldson Company, Inc. Refillable gas adsorption bed assembly and counterflow adsorber module
US5352274A (en) 1993-05-10 1994-10-04 Blakley Richard L Air filter and method
JP2750996B2 (en) 1993-09-08 1998-05-18 ニチアス株式会社 Organic solvent vapor adsorption device
US5407465A (en) * 1993-12-16 1995-04-18 Praxair Technology, Inc. Tuning of vacuum pressure swing adsorption systems
US5443625A (en) 1994-01-18 1995-08-22 Schaffhausen; John M. Air filtering fixture
US5389120A (en) 1994-02-08 1995-02-14 Sewell; Frederic D. Heating, ventilation and air conditioning unit with automatically controlled water spray air purification system
US5464369A (en) 1994-02-25 1995-11-07 Johnson Service Company Method and apparatus for estimating the rate at which a gas is generated within an enclosed space
JP2907026B2 (en) 1994-10-18 1999-06-21 三菱電機株式会社 Ventilation air conditioner
US6200542B1 (en) 1995-01-20 2001-03-13 Engelhard Corporation Method and apparatus for treating the atmosphere
US5564626A (en) 1995-01-27 1996-10-15 York International Corporation Control system for air quality and temperature conditioning unit with high capacity filter bypass
US5869323A (en) 1995-03-31 1999-02-09 Basys Technologies, Inc. Arrangement for air purification; and method
JP3416333B2 (en) 1995-05-10 2003-06-16 三菱重工業株式会社 Volatile organic matter recovery method
US5646304A (en) 1995-06-23 1997-07-08 The Boc Group, Inc. Process for the production of petrochemicals
US5672196A (en) 1995-08-01 1997-09-30 The Boc Group, Inc. Process and apparatus for the separation of gases
JP3088275B2 (en) 1995-09-27 2000-09-18 株式会社神戸製鋼所 Apparatus for removing nitrogen oxides from exhaust gas from automobile tunnels
US5614000A (en) 1995-10-04 1997-03-25 Air Products And Chemicals, Inc. Purification of gases using solid adsorbents
US5904896A (en) 1995-12-08 1999-05-18 A. R. Grindl Multi-stage zonal air purification system
US5675979A (en) 1996-03-01 1997-10-14 Honeywell Inc. Enthalpy based thermal comfort controller
US6649043B1 (en) 1996-08-23 2003-11-18 Exxonmobil Research And Engineering Company Regeneration of hydrogen sulfide sorbents
JPH1071323A (en) 1996-08-30 1998-03-17 Aqueous Res:Kk Air cleaning filter and air cleaner for car
US5876488A (en) * 1996-10-22 1999-03-02 United Technologies Corporation Regenerable solid amine sorbent
US5827355A (en) 1997-01-31 1998-10-27 Lockheed Martin Energy Research Corporation Carbon fiber composite molecular sieve electrically regenerable air filter media
US6432367B1 (en) 1997-02-28 2002-08-13 Michael Munk Indoor air quality gas phase return air cleaner
US6280691B1 (en) 1997-03-31 2001-08-28 Alliedsignal Inc. Indoor air purification system
US6027550A (en) 1997-04-28 2000-02-22 Techarmonic, Inc. Apparatus and method for removing volatile organic compounds from a stream of contaminated air with use of an adsorbent material
US5984198A (en) 1997-06-09 1999-11-16 Lennox Manufacturing Inc. Heat pump apparatus for heating liquid
US6187596B1 (en) 1997-07-11 2001-02-13 Donaldson Company, Inc. Airborne contaminant indicator
US5964927A (en) 1997-07-11 1999-10-12 Donaldson Company, Inc. Adsorption apparatus
NO329817B1 (en) 1998-04-02 2010-12-27 Mitsubishi Heavy Ind Ltd Process and apparatus for producing high concentration ozone gas
US6024781A (en) 1998-04-17 2000-02-15 The Boc Group, Inc. Separation of carbon dioxide and hydrocarbons
US6102793A (en) 1998-09-08 2000-08-15 Hansen; Michael Ventilation system
US6123617A (en) 1998-11-02 2000-09-26 Seh-America, Inc. Clean room air filtering system
US6120581A (en) 1999-01-13 2000-09-19 Uop Llc Sulfur production process
JP2000202232A (en) 1999-01-19 2000-07-25 Sekisui Chem Co Ltd Dehumidifier in housing part
JP2000291978A (en) 1999-04-06 2000-10-20 Daikin Ind Ltd Air conditioning apparatus
US20110064607A1 (en) 1999-05-28 2011-03-17 Thermapure, Inc. Method for removing or treating harmful biological organisms and chemical substances
US8256135B2 (en) 1999-05-28 2012-09-04 Thermapure, Inc. Method for removing or treating harmful biological and chemical substances within structures and enclosures
FR2795657B1 (en) 1999-07-02 2001-09-14 Air Liquide AIR PURIFICATION PROCESS BY ADSORPTION ON BARIUM-EXCHANGED ZEOLITE
IL130882A0 (en) 1999-07-11 2001-01-28 Solmecs Israel Ltd Sorbent composition
FR2798075B1 (en) * 1999-09-03 2001-11-09 Air Liquide CONDUCTING A THERMAL REGENERATION AIR PURIFICATION SYSTEM
US6797246B2 (en) 1999-09-20 2004-09-28 Danny L. Hopkins Apparatus and method for cleaning, neutralizing and recirculating exhaust air in a confined environment
ATE304952T1 (en) 1999-11-17 2005-10-15 Domnick Hunter Ltd AIR TREATMENT SYSTEM
JP3395077B2 (en) 1999-12-21 2003-04-07 新菱冷熱工業株式会社 Air conditioning system to improve indoor air quality
JP2001232127A (en) 2000-02-25 2001-08-28 Matsushita Seiko Co Ltd Automatic regenerating and filtering type dust collecting device
CN100455456C (en) 2000-03-09 2009-01-28 马里·德哈波特·林赛 Portable motor vehicle cabin air purifier
EP2269710A1 (en) 2000-05-05 2011-01-05 Entegris, Inc. Filters employing both acidic polymers and physical-adsorption media
US6564780B2 (en) 2000-06-23 2003-05-20 Toyota Jidosha Kabushiki Kaisha Diagnostic apparatus and method for fuel vapor purge system
DE60121339T2 (en) 2000-08-04 2007-08-09 Günter Rahn METHOD AND DEVICE FOR IMPROVING AIR QUALITY IN A BUILDING
US6364938B1 (en) 2000-08-17 2002-04-02 Hamilton Sundstrand Corporation Sorbent system and method for absorbing carbon dioxide (CO2) from the atmosphere of a closed habitable environment
US6755892B2 (en) * 2000-08-17 2004-06-29 Hamilton Sundstrand Carbon dioxide scrubber for fuel and gas emissions
US6375722B1 (en) * 2000-08-22 2002-04-23 Henderson Engineering Co., Inc. Heat of compression dryer
US6432376B1 (en) 2000-09-05 2002-08-13 Council Of Scientific & Industrial Research Membrane process for the production of hydrogen peroxide by non-hazardous direct oxidation of hydrogen by oxygen using a novel hydrophobic composite Pd-membrane catalyst
US6817359B2 (en) 2000-10-31 2004-11-16 Alexander Roger Deas Self-contained underwater re-breathing apparatus
US6711470B1 (en) 2000-11-16 2004-03-23 Bechtel Bwxt Idaho, Llc Method, system and apparatus for monitoring and adjusting the quality of indoor air
US6428608B1 (en) 2000-12-22 2002-08-06 Honeywell International Inc. Method and apparatus for controlling air quality
US6964692B2 (en) 2001-02-09 2005-11-15 General Motors Corporation Carbon monoxide adsorption for carbon monoxide clean-up in a fuel cell system
US6533847B2 (en) 2001-02-13 2003-03-18 Donaldson Company, Inc. Adsorption apparatus
JP4827307B2 (en) 2001-03-26 2011-11-30 矢崎総業株式会社 Air conditioner
CA2446020A1 (en) 2001-04-30 2002-11-07 The Regents Of The University Of Michigan Isoreticular metal-organic frameworks, process for forming the same, and systematic design of pore size and functionality therein, with application for gas storage
US6630012B2 (en) 2001-04-30 2003-10-07 Battelle Memorial Institute Method for thermal swing adsorption and thermally-enhanced pressure swing adsorption
US20020183201A1 (en) 2001-05-01 2002-12-05 Barnwell James W. Adsorbents for use in regenerable adsorbent fractionators and methods of making the same
ATE337070T1 (en) 2001-06-08 2006-09-15 Donaldson Co Inc ADSORPTION ELEMENT AND METHOD
US6503462B1 (en) 2001-06-19 2003-01-07 Honeywell International Inc. Smart air cleaning system and method thereof
US6872240B2 (en) 2001-07-10 2005-03-29 Peletex, Inc. Method and apparatus for filtering an air stream using an aqueous-froth together with nucleation
US20040005252A1 (en) 2001-07-20 2004-01-08 Siess Harold Edward Preventing the transmission of disease
US20030037672A1 (en) 2001-08-27 2003-02-27 Shivaji Sircar Rapid thermal swing adsorption
US6547854B1 (en) 2001-09-25 2003-04-15 The United States Of America As Represented By The United States Department Of Energy Amine enriched solid sorbents for carbon dioxide capture
EP1432455A1 (en) 2001-10-04 2004-06-30 The Johns Hopkins University Airborne pathogen neutralization
US6960179B2 (en) 2001-11-16 2005-11-01 National Quality Care, Inc Wearable continuous renal replacement therapy device
US6916239B2 (en) 2002-04-22 2005-07-12 Honeywell International, Inc. Air quality control system based on occupancy
US7077891B2 (en) 2002-08-13 2006-07-18 Air Products And Chemicals, Inc. Adsorbent sheet material for parallel passage contactors
US6796896B2 (en) 2002-09-19 2004-09-28 Peter J. Laiti Environmental control unit, and air handling systems and methods using same
JP3892387B2 (en) 2002-11-01 2007-03-14 松下エコシステムズ株式会社 Ventilation equipment
US6726558B1 (en) 2002-11-26 2004-04-27 Udi Meirav Oxygen enrichment of indoor human environments
US6866701B2 (en) 2002-11-26 2005-03-15 Udi Meirav Oxygen enrichment of indoor human environments
DE10300141A1 (en) 2003-01-07 2004-07-15 Blue Membranes Gmbh Method and device for oxygen enrichment of air with simultaneous depletion of carbon dioxide
CN2612444Y (en) 2003-04-17 2004-04-21 河南新飞电器有限公司 Air conditioner for removing carbon dioxide and replenishing oxygen using pressure changeable adsorption method
US6908497B1 (en) 2003-04-23 2005-06-21 The United States Of America As Represented By The Department Of Energy Solid sorbents for removal of carbon dioxide from gas streams at low temperatures
US7449053B2 (en) 2003-07-18 2008-11-11 David Richard Hallam Air filtration device
JP2005090941A (en) 2003-08-11 2005-04-07 Research Institute Of Innovative Technology For The Earth Air conditioning auxiliary device and air conditioning auxiliary method
KR100546367B1 (en) 2003-08-22 2006-01-26 삼성전자주식회사 Detector for identifying residual life time of absorbent, gas scrubber comprising the detector and method of identifying residual life time of absorbent
CA2454056C (en) 2003-12-23 2010-05-25 Venmar Ventilation Inc. Pressure equilizing system
BRPI0507155A (en) 2004-01-27 2007-06-26 Purifics Environmental Technol decontamination system; and method of decontaminating a medium
US7326388B2 (en) 2004-02-27 2008-02-05 Carrier Corporation Indoor air quality module with pivotal inner compartment for servicability of module components
WO2006088475A2 (en) 2004-05-10 2006-08-24 Precision Combustion, Inc. Regenerable adsorption system
CN2729562Y (en) 2004-06-04 2005-09-28 北京科技大学 Indoor air purification apparatus
JP4921367B2 (en) 2004-06-07 2012-04-25 インテグリス・インコーポレーテッド System and method for removing contaminants
US7189280B2 (en) 2004-06-29 2007-03-13 Questair Technologies Inc. Adsorptive separation of gas streams
CA2472752C (en) 2004-07-08 2008-01-15 Alexandre Gontcharov A method of controlling the concentration of purified nitrogen and oxygen in air conditioned space
JP2008510135A (en) 2004-08-11 2008-04-03 コーニンクレッカ フィリップス エレクトロニクス エヌ ヴィ Air pollution sensor system
US7416581B2 (en) 2004-09-03 2008-08-26 Point Source Solutions, Inc. Air-permeable filtration media, methods of manufacture and methods of use
US7331854B2 (en) 2004-10-13 2008-02-19 Lockheed Martin Corporation Common filtration unit for building makeup air and emergency exhaust
TWI300011B (en) 2004-11-10 2008-08-21 Ind Tech Res Inst Method and apparatus for treating inorganic acid gas
DE102004000050B4 (en) 2004-11-17 2008-07-31 Mann + Hummel Gmbh Filter element, in particular cabin filter, to the frontal flow
US7182805B2 (en) 2004-11-30 2007-02-27 Ranco Incorporated Of Delaware Corona-discharge air mover and purifier for packaged terminal and room air conditioners
US7820591B2 (en) 2005-01-04 2010-10-26 Korea Electric Power Corporation Highly attrition resistant and dry regenerable sorbents for carbon dioxide capture
US7288136B1 (en) 2005-01-13 2007-10-30 United States Of America Department Of Energy High capacity immobilized amine sorbents
US7472554B2 (en) 2005-02-14 2009-01-06 Continental Teves, Inc. Passenger environmental protection
JP2006275487A (en) 2005-03-30 2006-10-12 Shimizu Corp Carbon dioxide removing air conditioning system
MX2007012388A (en) 2005-04-07 2008-03-11 Univ Michigan High gas adsorption in a microporous metal-organic framework with open-metal sites.
US7413595B2 (en) 2005-04-08 2008-08-19 Air Products And Chemicals, Inc. Control scheme for hybrid PSA/TSA systems
US7311763B2 (en) 2005-04-22 2007-12-25 David Lloyd Neary Gas separation vessel apparatus
CN1865812A (en) 2005-05-19 2006-11-22 量子能技术股份有限公司 Heat pump system and method for heating a fluid
EP1984097A4 (en) 2005-06-15 2009-08-26 Questair Technologies Inc Adsorptive bulk separation for upgrading gas streams
US7645323B2 (en) 2005-08-16 2010-01-12 Oxyvital Limited Method and apparatus for improving the air quality within an enclosed space
US7862410B2 (en) 2006-01-20 2011-01-04 American Power Conversion Corporation Air removal unit
US20090220388A1 (en) 2006-02-07 2009-09-03 Battelle Memorial Institute Breathing air maintenance and recycle
US7891573B2 (en) 2006-03-03 2011-02-22 Micro Metl Corporation Methods and apparatuses for controlling air to a building
ITMI20060922A1 (en) 2006-05-10 2007-11-11 Finanziaria Unterland S P A EQUIPMENT AND METHOD FOR THE TREATMENT, PURIFICATION AND RE-CONDITIONING OF AIR WITHIN CONFINED ENVIRONMENTS AND WITH HUMAN PRESENCE
US7795175B2 (en) 2006-08-10 2010-09-14 University Of Southern California Nano-structure supported solid regenerative polyamine and polyamine polyol absorbents for the separation of carbon dioxide from gas mixtures including the air
DE102006048716B3 (en) 2006-10-14 2008-02-21 Howaldswerke Deutsche Werft Ag Submarine boat comprises carbon dioxide binding unit for binding carbon dioxide contained in air inside submarine, where binding unit has carbon dioxide binding medium, and steam generator is provided for producing water vapors
CN200993448Y (en) 2006-11-22 2007-12-19 和舰科技(苏州)有限公司 Make-up air unit hot coiled pipe humidifying enthalpygain energy-saving device
US7855261B2 (en) 2006-12-08 2010-12-21 Eastman Chemical Company Aldehyde removal
CN101199913A (en) 2006-12-11 2008-06-18 蔡铭昇 Absorption processing system of volatile organic compounds
WO2008086489A2 (en) 2007-01-10 2008-07-17 Karamanos John C Embedded heat exchanger for heating, ventilation, and air conditioning (hvac) systems and methods
US20080173035A1 (en) 2007-01-22 2008-07-24 Thayer Daniel D Split system dehumidifier
US20080182506A1 (en) 2007-01-29 2008-07-31 Mark Jackson Method for controlling multiple indoor air quality parameters
GB2482454B (en) 2007-03-09 2012-05-16 Strata Products Worldwide Llc Apparatus, system and method for cleaning air
US7802443B2 (en) 2007-04-13 2010-09-28 Air Innovations, Inc. Total room air purification system with air conditioning, filtration and ventilation
WO2008155543A2 (en) 2007-06-18 2008-12-24 Thermal Energy Systems Ltd Heat pump
EP2164812A4 (en) 2007-06-22 2011-08-03 Carrier Corp Purification of a fluid using ozone with an adsorbent and/or a particle filter
EP2008679A1 (en) 2007-06-28 2008-12-31 General Electric Company Patient breathing system
AR068841A1 (en) 2007-10-12 2009-12-09 Union Engeneering As REMOVAL OF CARBON DIOXIDE FROM A POWER GAS
CN101848754A (en) 2007-11-05 2010-09-29 环球研究技术有限公司 Removal of carbon dioxide from air
US7666077B1 (en) 2007-11-13 2010-02-23 Global Finishing Solutions, L.L.C. Paint booth arrangement and method for directing airflow
JP4505498B2 (en) 2007-12-21 2010-07-21 株式会社トーエネック Heat source performance evaluation system for air conditioning
US20090188985A1 (en) 2008-01-30 2009-07-30 Scharing Michael G Combined chiller and boiler HVAC system in a single outdoor operating unit
JP2009202137A (en) 2008-02-29 2009-09-10 Mitsubishi Electric Corp Air treatment apparatus
US8591627B2 (en) * 2009-04-07 2013-11-26 Innosepra Llc Carbon dioxide recovery
CA2726383C (en) 2008-04-06 2015-08-25 Innosepra Llc Carbon dioxide recovery
US20090260372A1 (en) 2008-04-18 2009-10-22 Hunter Manufacturing Co. Systems and methods of heating, cooling and humidity control in air filtration adsorbent beds
US7846237B2 (en) 2008-04-21 2010-12-07 Air Products And Chemicals, Inc. Cyclical swing adsorption processes
WO2009149292A1 (en) 2008-06-04 2009-12-10 Global Research Technologies, Llc Laminar flow air collector with solid sorbent materials for capturing ambient co2
CN101596390A (en) 2008-06-06 2009-12-09 唐忠联 Air cleaning unit
US8317890B2 (en) 2008-08-29 2012-11-27 Donaldson Company, Inc. Filter assembly; components therefor; and, methods
US8118914B2 (en) * 2008-09-05 2012-02-21 Alstom Technology Ltd. Solid materials and method for CO2 removal from gas stream
US8078326B2 (en) 2008-09-19 2011-12-13 Johnson Controls Technology Company HVAC system controller configuration
CA2640152A1 (en) 2008-10-03 2010-04-03 Claude Beaule Co2 extractor
US8936727B2 (en) * 2009-03-06 2015-01-20 Uop Llc Multiple bed temperature controlled adsorption
CN101444693B (en) 2008-12-19 2011-03-02 哈尔滨工业大学 Method for activated carbon fiber variable voltage desorption gas
JP5058964B2 (en) 2008-12-26 2012-10-24 株式会社モリカワ Adsorption / desorption apparatus and adsorption / desorption method for air containing volatile organic compound gas
EP2266680A1 (en) 2009-06-05 2010-12-29 ETH Zürich, ETH Transfer Amine containing fibrous structure for adsorption of CO2 from atmospheric air
CN201363833Y (en) 2009-03-12 2009-12-16 李燕 Centralized air processor
US9020647B2 (en) 2009-03-27 2015-04-28 Siemens Industry, Inc. System and method for climate control set-point optimization based on individual comfort
WO2010124388A1 (en) 2009-05-01 2010-11-04 Mark Clawsey Ventilator system for recirculation of air and regulating indoor air temperature
US8328904B2 (en) 2009-05-04 2012-12-11 Bry-Air, Inc. Method and system for control of desiccant dehumidifier
US8491705B2 (en) 2009-08-19 2013-07-23 Sunho Choi Application of amine-tethered solid sorbents to CO2 fixation from air
US8388736B2 (en) 2009-10-02 2013-03-05 Perkinelmer Health Sciences, Inc. Sorbent devices and methods of using them
US8980171B2 (en) 2009-10-13 2015-03-17 David W. Mazyck System and method for purifying air via low-energy, in-situ regenerated silica-titania composites
MY165472A (en) * 2009-11-02 2018-03-23 Teijin Pharma Ltd Oxygen enrichment device
US8361205B2 (en) 2009-12-23 2013-01-29 Praxair Technology, Inc. Modular compact adsorption bed
US20110192172A1 (en) 2010-01-07 2011-08-11 Moises Aguirre Delacruz Temperature conditioning system method to optimize vaporization applied to cooling system
US8685153B2 (en) 2010-01-26 2014-04-01 Micropore, Inc. Adsorbent system for removal of gaseous contaminants
EP2545334B8 (en) 2010-03-10 2018-09-19 ADA-ES, Inc. Process for dilute phase injection of dry alkaline materials into a gas
CA2828602A1 (en) 2010-03-16 2011-09-22 Martin Mittelmark Plant air purification enclosure apparatus and method
CN201618493U (en) 2010-03-18 2010-11-03 美泰克(天津)矿物有限公司 Air purification system
GB201004638D0 (en) 2010-03-19 2010-05-05 Univ Belfast Separation of gases
WO2011130129A1 (en) 2010-04-13 2011-10-20 Conocophillips Company Ammonia salts as regenerable co2 sorbents
US20110269919A1 (en) 2010-04-28 2011-11-03 Nanomaterial Innovation Ltd. CO2 reservoir
PL2563495T3 (en) 2010-04-30 2020-05-18 Peter Eisenberger Method for carbon dioxide capture
US20110277490A1 (en) 2010-05-17 2011-11-17 Udi Meirav Method and System for Improved-Efficiency Air-Conditioning
FR2960448B1 (en) 2010-05-25 2012-07-20 Saint Gobain Quartz Sas METHOD AND DEVICE FOR PURIFYING THE AIR
ES2488123T3 (en) 2010-06-15 2014-08-26 Astrium Gmbh Procedure for the regeneration of an adsorption medium or absorption medium
US8425673B2 (en) 2010-07-16 2013-04-23 Solution Dynamics Regenerative dryers with a bypass
US8763478B2 (en) 2010-09-07 2014-07-01 Unibest International, Llc Environmental sampler and methods of using same
CN202270445U (en) 2010-11-11 2012-06-13 飞利浦(中国)投资有限公司 Air filtering device
US9101866B2 (en) 2010-11-16 2015-08-11 Gregory R. Miller Room air purifier
US8697451B2 (en) 2010-11-22 2014-04-15 Fuelcell Energy, Inc. Sulfur breakthrough detection assembly for use in a fuel utilization system and sulfur breakthrough detection method
JP6034794B2 (en) 2010-11-24 2016-11-30 ブルテック・リミテッド・ライアビリティ・カンパニーBlutec,Llc Air purification system
US20120148858A1 (en) 2010-12-10 2012-06-14 Valspar Sourcing, Inc. Coating composition for aldehyde abatement
US20120152116A1 (en) 2010-12-16 2012-06-21 Prometheus Technologies, Llc Rotary fluid processing systems and associated methods
CN103476489B (en) 2011-01-07 2016-08-10 阿克伦大学 The renewable solid absorbent of immobilization amine of low cost
ES2616028T3 (en) 2011-01-20 2017-06-09 Saudi Arabian Oil Company Reversible adsorption method on solid and system that uses residual heat for recovery and storage on board CO2
US8690999B2 (en) 2011-02-09 2014-04-08 Enverid Systems, Inc. Modular, high-throughput air treatment system
AU2012223684B2 (en) 2011-02-28 2017-04-20 Corning Incorporated Article for carbon dioxide capture
ES2387791B1 (en) 2011-03-04 2013-09-02 Endesa S A CO2 CAPTURE PROCEDURE
CN202032686U (en) 2011-03-07 2011-11-09 上海三因环保科技有限公司 System for controlling ambient atmosphere
WO2012139023A2 (en) 2011-04-06 2012-10-11 The Research Foundation Of State University Of New York Device and method for determining processing capacity
BR112013026815A2 (en) 2011-04-18 2017-12-12 Ryncosmos Llc method and apparatus for the removal of carbon dioxide from exhaust gases from automobiles, households and industries
US20120271460A1 (en) 2011-04-22 2012-10-25 Rognli Roger W Universal demand-response remote control for ductless split system
CN102233217A (en) 2011-04-30 2011-11-09 林勇 Automatic dust removal device for filter screen of air conditioner
FR2975075B1 (en) 2011-05-12 2013-06-28 Dcns SUBMARINE ENGINE ASSEMBLY WITH AN AMBIENT GAS TREATMENT SYSTEM AND PROCESSING METHOD THEREOF
CN108579706A (en) 2011-05-17 2018-09-28 恩弗里德系统公司 Sorbent for reducing carbon dioxide from room air
CN102784524B (en) 2011-05-20 2014-12-10 雅高思先进科技有限公司 High-performance air cleaning device and method
JP5812694B2 (en) * 2011-05-31 2015-11-17 川崎重工業株式会社 Carbon dioxide recovery method and apparatus
US20120321511A1 (en) 2011-06-20 2012-12-20 Lorcheim Paul W Gaseous chlorine dioxide decontamination system and method
US9403116B2 (en) 2011-07-18 2016-08-02 Carrier Corporation Regenerative scrubber system with single flow diversion actuator
US9316410B2 (en) 2011-11-17 2016-04-19 Enverid Systems, Inc. Method and system for conditioning air in an enclosed environment with distributed air circulation systems
US8999045B2 (en) 2012-01-05 2015-04-07 Suburban Manufacturing, Inc. Regenerative air dryer
WO2013106573A1 (en) 2012-01-10 2013-07-18 Enverid Systems, Inc Methods and systems for managing air quality and energy use in air-conditioning systems
US20150078964A1 (en) 2012-04-10 2015-03-19 Enverid Systems, Inc. Volatile organic compound remover assembly
US8734571B2 (en) 2012-05-31 2014-05-27 Air Products And Chemicals, Inc. Purification of air
US9927535B2 (en) 2012-06-06 2018-03-27 Siemens Industry, Inc. Radon detection and mitigation in a building automation system
US9950290B2 (en) 2012-07-18 2018-04-24 Enverid Systems, Inc. Systems and methods for regenerating adsorbents for indoor air scrubbing
CN104685300B (en) 2012-09-24 2017-11-28 恩沃德系统公司 Air treatment system with integration air processing
US9987584B2 (en) 2012-11-15 2018-06-05 Enverid Systems, Inc. Method and system for reduction of unwanted gases in indoor air
EP2976146A4 (en) 2013-03-18 2016-11-16 Enverid Systems Inc Systems and methods of cleaning cabin air in a transportation vehicle
US9802148B2 (en) 2013-04-23 2017-10-31 Enverid Systems, Inc. Regenerable sorbent CO2 scrubber for submarine vessels
EP3046648A4 (en) 2013-09-16 2017-04-05 Enverid Systems Inc. Method and system for filtering formaldehyde from indoor air
WO2015042150A1 (en) 2013-09-17 2015-03-26 Enverid Systems, Inc. Systems and methods for efficient heating of sorbents in an indoor air scrubber
SE540952C2 (en) 2014-08-05 2019-01-08 Corroventa Avfuktning Ab Method and apparatus for dehumidification
WO2016183237A1 (en) 2015-05-11 2016-11-17 Enverid Systems, Inc. Method and system for reduction of unwanted gases in indoor air
US10792608B2 (en) 2015-08-24 2020-10-06 Enverid Systems, Inc. Scrubber for HVAC system
WO2017087699A1 (en) 2015-11-18 2017-05-26 Enverid Systems, Inc. Method, devices and systems for radon removal from indoor areas
US11207633B2 (en) 2016-04-19 2021-12-28 Enverid Systems, Inc. Systems and methods for closed-loop heating and regeneration of sorbents
WO2017219043A1 (en) 2016-06-17 2017-12-21 Enverid Systems, Inc. Apparatus, methods and systems for multi-stage scrubbing of gas mixtures
CN109952140A (en) 2016-11-10 2019-06-28 恩弗里德系统公司 The room air washer that low noise, ceiling are installed
EP3444535A1 (en) 2017-08-15 2019-02-20 Koninklijke Philips N.V. Ventilation unit, system and method

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4816043A (en) * 1985-05-31 1989-03-28 Wilkerson Coporation Adsorption-desorption fluid fractionation with cycle phase switching controlled by purge and saturation front conditions
US20120160099A1 (en) * 2009-07-27 2012-06-28 Kawasaki Jukogyo Kabushiki Kaisha Carbon dioxide separation method and apparatus
US8157892B2 (en) * 2010-05-17 2012-04-17 Enverid Systems, Inc. Method and system for improved-efficiency air-conditioning
US9566545B2 (en) * 2012-05-22 2017-02-14 Enverid Systems, Inc. Efficient use of adsorbents for indoor air scrubbing
US10525401B2 (en) * 2012-05-22 2020-01-07 Enverid Systems, Inc. Efficient use of adsorbents for indoor air scrubbing
US11541346B2 (en) * 2012-05-22 2023-01-03 Enverid Systems, Inc. Efficient use of adsorbents for indoor air scrubbing

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US11890571B2 (en) 2012-11-15 2024-02-06 Enverid Systems, Inc. Method and system for reduction of unwanted gases in indoor air

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