EP4161684A1 - Systèmes et procédés biologiques de récolte et de culture d'algues - Google Patents

Systèmes et procédés biologiques de récolte et de culture d'algues

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Publication number
EP4161684A1
EP4161684A1 EP21821515.0A EP21821515A EP4161684A1 EP 4161684 A1 EP4161684 A1 EP 4161684A1 EP 21821515 A EP21821515 A EP 21821515A EP 4161684 A1 EP4161684 A1 EP 4161684A1
Authority
EP
European Patent Office
Prior art keywords
permeate
backwash
algae
valve
tank
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
EP21821515.0A
Other languages
German (de)
English (en)
Inventor
David A. Hazlebeck
William Rickman
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Global Algae Technology LLC
Original Assignee
Global Algae Technology LLC
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Priority claimed from US16/896,632 external-priority patent/US11767501B2/en
Application filed by Global Algae Technology LLC filed Critical Global Algae Technology LLC
Publication of EP4161684A1 publication Critical patent/EP4161684A1/fr
Pending legal-status Critical Current

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Classifications

    • C—CHEMISTRY; METALLURGY
    • C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12M—APPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M21/00—Bioreactors or fermenters specially adapted for specific uses
    • C12M21/02—Photobioreactors
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/14—Ultrafiltration; Microfiltration
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
    • B01D61/14—Ultrafiltration; Microfiltration
    • B01D61/22—Controlling or regulating
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D63/00—Apparatus in general for separation processes using semi-permeable membranes
    • B01D63/02—Hollow fibre modules
    • C—CHEMISTRY; METALLURGY
    • C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12M—APPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M33/00—Means for introduction, transport, positioning, extraction, harvesting, peeling or sampling of biological material in or from the apparatus
    • C12M33/14—Means for introduction, transport, positioning, extraction, harvesting, peeling or sampling of biological material in or from the apparatus with filters, sieves or membranes
    • C—CHEMISTRY; METALLURGY
    • C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12M—APPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M47/00—Means for after-treatment of the produced biomass or of the fermentation or metabolic products, e.g. storage of biomass
    • C12M47/02—Separating microorganisms from the culture medium; Concentration of biomass
    • C—CHEMISTRY; METALLURGY
    • C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
    • C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
    • C12N1/02—Separating microorganisms from their culture media
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2311/00—Details relating to membrane separation process operations and control
    • B01D2311/06—Specific process operations in the permeate stream
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2311/00—Details relating to membrane separation process operations and control
    • B01D2311/26—Further operations combined with membrane separation processes
    • B01D2311/2688—Biological processes
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2313/00—Details relating to membrane modules or apparatus
    • B01D2313/18—Specific valves
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2313/00—Details relating to membrane modules or apparatus
    • B01D2313/48—Mechanisms for switching between regular separation operations and washing
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2315/00—Details relating to the membrane module operation
    • B01D2315/06—Submerged-type; Immersion type
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2315/00—Details relating to the membrane module operation
    • B01D2315/18—Time sequence of one or more process steps carried out periodically within one apparatus
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2315/00—Details relating to the membrane module operation
    • B01D2315/20—Operation control schemes defined by a periodically repeated sequence comprising filtration cycles combined with cleaning or gas supply, e.g. aeration
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2321/00—Details relating to membrane cleaning, regeneration, sterilization or to the prevention of fouling
    • B01D2321/04—Backflushing
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2321/00—Details relating to membrane cleaning, regeneration, sterilization or to the prevention of fouling
    • B01D2321/12—Use of permeate
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/80—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in fisheries management

Definitions

  • This present disclosure relates generally to systems and methods for solid or biological slurry filtration, harvesting and cultivation, and more specifically to algae harvesting and cultivation systems and methods.
  • Electrocoagulation, cross flow filtration, bioflocculation, vibrating membrane filtration and ultrasonic harvesting have been proposed as alternatives to centrifuges and air flotation systems, but an algae harvesting system having low operating costs and minimal energy requirements has remained elusive.
  • One approach to general solid separation has been outside-in hollow-fiber dead-end filtration in an atmospheric pressure system. These systems include multiple porous hollow fibers, which can be grouped or arranged into modules. The modules can be grouped into cassettes having multiple modules, and the cassettes can be grouped into banks of multiple cassettes. The hollow fibers are immersed in a liquid suspension, and filtrate or permeate can be drawn through walls of the fibers and out of the fiber lumens.
  • a concentrate or retentate with the retained solids remains outside of the hollow fibers.
  • the fibers can be arranged vertically, horizontally, or at an intermediate angle in the liquid suspension.
  • modules are typically contained in concrete basins or tanks made of metal or plastic to minimize the amount of extra fluid in the system, attain higher concentrations of solids, and reduce the amount of fluid required for membrane washing and cleaning.
  • very high volumetric flows are used, resulting in high costs for concrete basins or tanks to contain the hollow-fiber membranes.
  • Membrane fouling is a significant problem with these hollow fiber dead-end filtration systems.
  • membrane fouling occurs when a solution or particle gets deposited on a surface or in the pores of a membrane causing the membrane's filtration performance to be degraded.
  • Typical methods to reduce membrane fouling with hollow fiber membranes include introduction of air bubbles around the hollow fibers of the membrane, moving the hollow fibers within the liquid suspension, periodic backwashing (also called back- pulsing or backflushing), periodic chemical cleaning, and periodic draining of the liquid suspension.
  • Backwashing is a process in which a fluid is forced through the fibers of the modules typically at a flow rate that is greater than the rate at which permeate is withdrawn.
  • Fibers may be backwashed with a liquid such as water, or a gas (e.g., air) or a mixture of gas and liquid.
  • a liquid such as water, or a gas (e.g., air) or a mixture of gas and liquid.
  • the backwash is essentially a recycling process in which the solids production rate is sacrificed during the backwash and during the time it takes to re-filter the water or permeate that was used for the backwash.
  • a water or permeate based backwash system is therefore justified primarily when the cleaning effect is significant.
  • the maximum delta or change in pressure for backwashing or permeate flow is typically about eight pounds per square inch (psi), so controls are needed on the pumps to prevent over-pressurizing the membranes and to control the variation in pressure when the permeate and backwash valves are opened and closed.
  • Periodic backwashing is typically utilized several times per hour in solid filtration systems, e.g. backwash intervals of 15-30 minutes.
  • the backwash offline period is typically 30- 120 second and can include the time to open and close valves, the time for the backwash fluid to flow, and the time for any pulsing or adjusting of any pump or compressor during the backwash flow.
  • the backwash process is essentially a recycling process in which the solid production rate is sacrificed during the backwash off-line period and during the time to re-filter the water or the permeate that was used in the backwash. Backwashing is therefore justified to the extent that the cleaning effect is significant. Attempts to optimize backwashing in hollow fiber dead-end filtration systems have indicated that as suspended solids concentration is increased, the backwash off-line period is typically increased to allow for a longer time for backwash flow.
  • VFD variable frequency drive
  • the backwash pressure in hollow fiber membranes is limited to avoid damaging the fiber membranes.
  • the backwash pressure used in hollow fiber membrane systems is typically well below the maximum to avoid membrane damage from spikes or transients when the backwash is started and stopped. Complicated controls are required to minimize these transients and pressure spikes.
  • the low-pressure tolerance of hollow fibers prevents the use of short, high- pressure back-pulses that are used in ceramic or metallic membrane systems to remove fouling by a pressure shock.
  • Biological slurries such as algae or activated sludge are typically more difficult to filter to high suspended solids concentrations than inorganic slurries.
  • Natural or synthetic flocculants are typically required to attain greater than 1% suspended solids. The addition of flocculent, however, is costly and can negatively impact the processing or value of the algae product.
  • Activated sludge is a consortium of microbes in which natural bioflocculation is attained, so hollow fiber dead-end filtration can be used for activated sludge.
  • the maximum concentration of suspended solids with naturally flocculated activated sludge is typically about 3% to 4.5% when dead-end hollow fiber filtration is used for activated sludge.
  • Non-flocculent, cross-flow membrane filtration systems have been used in an attempt to attain a high concentration of algae product.
  • Cross-flow filtration systems have higher energy requirements and higher operating costs than dead-end filtration systems.
  • typical cross-flow filtration systems can require .4 to 7 kWh/mB of energy to operate.
  • Cross-flow filtration systems are therefore less economical than dead-end hollow fiber systems.
  • cross-flow systems have higher shear stress and have recirculation in the cross flow pump loop, which can damage algae cells.
  • Multistage hollow fiber solid filtrations systems have been used with constant flux in each stage to achieve higher average flux.
  • These constant flux and constant area multistage systems typically produce low solid concentration (e.g., less than 1% suspended solids), and require active transmembrane pressure control and active fluid flowrate control for each stage, which increases the cost and complexity of such systems.
  • Production of algal products is often enhanced by two-stage cultivation in which algae is pretreated before entering a second stage or the algae media is altered in the second stage.
  • stress from media changes such as nitrogen deprivation, salinity, or pH is used to induce formation of a product.
  • exposure to stress such as shear, ozone, bleach, or high light is used to induce formation of a product. If the media is changed, then recovery and recycle of the media for cultivation is prevented because salts or other dissolved solids are added to the media, and high operating costs are incurred because chemicals must be added to each batch to modify the media. If exposure to stress is used, then the amount of chemicals or size of the second stage pretreatment system is large because the algae are cultivated under dilute conditions.
  • Aquaculture facilities often require live feeds to feed fish, shellfish, and larva of fish or shellfish. These algae could be produced more economically in centralized facilities, but shipment of dilute cultures is expensive, and algae harvesting processes damage the algae or require flocculants, so concentrated algae cultures are not available. Dead algae products are centrally produced and shipped for use in aquaculture facilities, but these products are not as effective as live algae. Thus, typical aquaculture facilities must cultivate algae for feed in addition to cultivating fish or shellfish.
  • an algae harvesting system provides at least one treatment tank and at least one membrane filtration module positioned inside the at least one treatment tank.
  • the filtration module includes a plurality of hollow fiber membranes defining lumens.
  • the system is configured to perform dead-end filtration of an algae slurry contained in the treatment tank by pulling a substantially algae-free permeate through pores of the plurality of hollow fiber membranes so that the permeate flows inside the lumens of the hollow fiber membranes and a retentate of the algae slurry is produced outside the lumens of the hollow fiber membranes.
  • the system is further configured to perform a backwash sequence in which a backwash fluid flows inside the lumens of the hollow fiber membranes and is pushed through the pores of the hollow fiber membranes to remove any foulants that have accumulated on the hollow fiber membrane.
  • the backwash sequence includes an off-line period of less than about twelve seconds.
  • an algae harvesting system provides at least one treatment tank and at least one membrane filtration module positioned inside the treatment tank.
  • the filtration module includes a plurality of hollow fiber membranes defining lumens.
  • the system is configured to perform dead-end filtration of an algae slurry contained in the treatment tank by pulling a substantially algae-free permeate through pores of the hollow fiber membranes so that the permeate flows inside the lumens of the hollow fiber membranes and a retentate of the algae slurry is produced outside the lumens of the hollow fiber membranes.
  • the system is further configured to perform a backwash sequence in which a backwash fluid flows inside the lumens of the hollow fiber membranes and is pushed through the pores of the hollow fiber membranes to remove any foulants that have accumulated on the plurality of hollow fiber membranes.
  • the backwash sequence includes an interval of less than about three minutes, and the interval includes the time between the start of one backwash cycle and the start of a next backwash cycle.
  • an algae harvesting method includes, in a dead end filtration process, pulling a substantially algae-free permeate from an algae slurry through pores of a plurality of hollow fiber membranes positioned inside the treatment tank so that the permeate flows inside lumens of the hollow fiber membranes and a retentate of the algae slurry is produced outside the lumens of the plurality of hollow fiber membranes.
  • the method further includes, in a backwash sequence, pushing a backwash fluid through pores of the hollow fiber membranes to remove any foulants that have accumulated on the plurality of hollow fiber membranes.
  • the backwash sequence includes an interval of less than about three minutes and an off-line period of less than about twelve seconds.
  • an algae harvesting system provides at least one treatment tank defining a plurality of filtration stages including a first filtration stage and a second filtration stage.
  • the first filtration stage includes a first membrane filtration module positioned inside the treatment tank.
  • the first membrane filtration module includes a first plurality of hollow fiber membranes having a first total outside filtration area and defining lumens.
  • the first module also includes a retentate outlet, and a permeate outlet.
  • the second filtration stages includes a second at membrane filtration module positioned inside the treatment tank.
  • the second membrane filtration module includes a second plurality of hollow fiber membranes having a second total outside filtration area and defining lumens.
  • the second module also includes an inlet coupled fluidly to the retentate outlet of the first filtration stage, a retentate outlet, and a permeate outlet.
  • the system is configured to perform dead-end filtration of an algae slurry in the treatment tank by pulling permeate through pores of the first hollow fiber membranes at a first flux so that the permeate flows inside the lumens of the first hollow fiber membranes and a first retentate is produced outside the lumens of the first hollow fiber membranes, allowing at least a portion of the first retentate to flow from the retentate outlet of the first filtration stage to the inlet of the second filtration stage, and (iii) pulling permeate through pores of the second hollow fiber membranes at a second different flux so that the permeate flows inside the lumens of the second hollow fiber membranes and a second retentate is produced outside the lumens of the second hollow fiber membranes.
  • an algae harvesting method for performing dead-end filtration in an algae harvesting system having at least one treatment tank defining a plurality of filtration stages including at least a first filtration stage and a second filtration stage, wherein the first filtration stage has a first plurality of hollow fiber membranes positioned inside the at least one treatment tank and the second filtration stage has a second plurality of hollow fiber membranes positioned inside the at least one treatment tank.
  • the method includes in a dead-end filtration process, pulling permeate at the first filtration stage from an algae slurry through pores of the first hollow fiber membranes at a first flux so that the permeate flows inside the lumens of the first a plurality of hollow fiber membranes and a first retentate is produced outside the lumens of the first hollow fiber membranes and flowing the first retentate from the first filtration stage to the second filtration stage.
  • the method additionally includes, in a dead-end filtration process and in fluid parallel with the pulling in the first filtration stage, pulling at the second filtration stage a permeate from the algae slurry through pores of the second plurality of hollow fiber membranes at a second different flux so that a second retentate is produced outside the lumens of the second plurality of hollow fiber membranes.
  • an algae harvesting system provides at least one treatment tank having an algae slurry feed inlet, and a retentate outlet.
  • the system further includes (i) at least one membrane filtration module positioned inside the treatment tank, wherein the membrane filtration module includes a plurality of hollow fiber membranes defining lumens (ii) a permeate tank positioned such that a level of permeate fluid contained in the permeate tank is below a level of algae slurry contained in the at least one treatment tank; (iii) at least one permeate conduit coupled fluidly to the permeate tank and to the plurality of hollow fiber membranes; and (iii) a gas purge conduit coupled fluidly to the at least one permeate conduit such that a pressure increase in the at least one permeate conduit also increases a pressure in the at least one purge conduit so that any gas that has accumulated in the at least one permeate conduit can be pushed through the gas purge conduit.
  • the system is configured to perform dead-end filtration of the algae slurry contained in the treatment tank by siphoning a substantially algae-free permeate through pores of the plurality of hollow fiber membranes so that the permeate flows inside the lumens of the hollow fiber membranes, through the permeate conduit to the permeate tank, and a retentate of the algae slurry is produced outside the lumens of the hollow fiber membranes.
  • the system is further configured to perform a backwash sequence in which (a) a backwash fluid flows inside the lumens of the hollow fiber membranes and is pushed through the pores of the hollow fiber membranes to remove any foulants that have accumulated on the hollow fiber membranes, and (b) any gas in the at least one permeate conduit is pushed through the gas purge conduit.
  • an algae harvesting system including (i) at least one treatment tank for an algae slurry, (ii) at least one membrane filtration module positioned inside the treatment tank, the membrane filtration module including a plurality of hollow fiber membranes defining lumens; (iii) a backwash tank positioned such that a level of backwash fluid contained in the backwash tank is above a level of the algae slurry in the treatment tank, and (iv) at least one backwash conduit coupled fluidly to the backwash tank and to the hollow fiber membranes.
  • the system is configured to perform dead-end filtration of the algae slurry in the treatment tank by pulling a substantially algae-free permeate through pores of the plurality of hollow fiber membranes so that the permeate flows inside the lumens of the plurality of hollow fiber membranes and a retentate of the algae slurry is produced outside the lumens of the hollow fiber membranes.
  • the system is further configured to perform a backwash sequence in which the backwash liquid (a) gravity flows from the backwash tank, through the backwash conduit, to inside the lumens of the plurality of hollow fiber membranes, and (b) is pushed through the pores of the plurality of hollow fiber membranes to remove any foulants that have accumulated on the plurality of hollow fiber membranes.
  • an algae harvesting system provides (i) at least one treatment tank, (ii) a cassette positioned inside the at least one treatment tank, wherein the cassette includes a plurality of membrane filtration modules coupled fluidly in parallel via a cassette header, wherein each of the filtration modules has hollow fiber membranes defining lumens, and wherein the total outside surface area of all of the hollow fiber membranes of the cassette is about 500 m 2 to 2200 m 2 , (iii) a single permeate valve coupled fluidly to the header; and (iv) a single backwash valve coupled fluidly to the header.
  • the system is configured to perform dead-end filtration of an algae slurry contained in the treatment tank by pulling permeate through pores of the hollow fiber membranes so that the permeate flows inside the lumens of the hollow fiber membranes and retentate is produced outside the lumens of the hollow fiber membranes.
  • the system is further configured to perform a backwash sequence in which a backwash fluid flows inside the lumens of the hollow fiber membranes and is pushed through the pores of the hollow fiber membranes so as to remove any foulants that have accumulated on the hollow fiber membranes, wherein the actuation time for the single backwash valve and the single permeate valve is about three seconds or less, and the actuation time includes the time to (i) open the single backwash valve and the single permeate valve or (ii) close the single backwash valve and the single permeate valve.
  • an algae harvesting system provides (i) at least one treatment tank; (ii) a bank positioned inside the at treatment tank, wherein the bank includes a first cassette and a second cassette, wherein the first cassette and the second cassette are coupled fluidly in parallel via a bank header, wherein the first cassette includes a first plurality of membrane filtration modules coupled fluidly in parallel via a first cassette header and the second cassette includes a second plurality of membrane filtration modules coupled fluidly in parallel via a second cassette header, wherein each of the first and second plurality of membrane filtration modules has hollow fiber membranes defining lumens, and wherein the total outside surface area of all of the hollow fiber membranes of the bank is about 500 m 2 to 10,000 m 2 ; (iii) a single permeate valve coupled fluidly to the bank header; and (iv) a single backwash valve coupled fluidly to the bank header.
  • the system is configured to perform dead-end filtration of an algae slurry in the treatment tank by pulling permeate through pores of the hollow fiber membranes so that the permeate flows inside the lumens of the hollow fiber membranes and a retentate is produced outside the lumens of the hollow fiber membranes.
  • the system is further configured to perform a backwash sequence in which a backwash fluid flows inside the lumens of the hollow fiber membranes and is pushed through the pores of the hollow fiber membranes so as to remove any foulants that have accumulated on the hollow fiber membranes, wherein the actuation time for the single backwash valve and the single permeate valve is about three seconds or less, and the actuation time includes the time to (i) open the single backwash valve and the single permeate valve or (ii) close the single backwash valve and the single permeate valve.
  • an algae harvesting system provides a first lined earthen treatment tank defining a first filtration stage and a second treatment tank defining a second filtration stage.
  • the first filtration stage includes (i) a first at least one membrane filtration module positioned inside the earthen treatment tank, wherein the first filtration module includes first hollow fiber membranes having a first total outside filtration area and defining lumens, (ii) a retentate outlet, and (iii) a permeate outlet.
  • the second filtration stage includes (i) a second at least one membrane filtration module positioned inside the second treatment tank, wherein second filtration module includes second hollow fiber membranes having a second total outside filtration area and defining lumens, (ii) an inlet coupled fluidly with the retentate outlet of the first filtration stage, (iii) a retentate outlet, and (iv) a permeate outlet.
  • the system is configured to perform dead-end filtration of an algae slurry contained in the earthen treatment tank and the second treatment tank by pulling permeate through pores of the first and second plurality of hollow fiber membranes so that retentate is produced outside the lumens of the first and second plurality of hollow fiber membranes.
  • an algae harvesting and cultivation system provides a first algae cultivator defining a first cultivation stage, wherein the first cultivation stage includes a first at least one cultivation device having a first algae cultivation media for cultivating algae.
  • the algae harvesting and cultivation system further provides a first dead-end filtration system in fluid communication with the first cultivation stage such that the first dead-end filtration system receives at least a portion of the algae cultivated from the first cultivation stage, wherein the first dead-end filtration system has a first plurality of hollow fiber membranes and is configured to dead-end filter the algae received from the first cultivation stage through the first plurality of hollow fiber membranes so as to produce a first retentate and a first permeate.
  • the algae harvesting and cultivation system is constructed and arranged such that the first permeate flows back to the first cultivation stage.
  • the algae harvesting and cultivation system further includes a second algae cultivator defining a second cultivation stage, wherein the second cultivation stage is in fluid communication with the first dead-end filtration system such that the second cultivation stage receives the first retentate, wherein the second cultivation stage includes a second at least one cultivation device having a second media for cultivating additional algae using the first retentate.
  • the algae harvesting and cultivation system further includes a second dead-end filtration system in fluid communication with the second cultivation stage such that the second dead-end filtration system receives at least a portion of the additional algae cultivated in the second cultivation stage, wherein the second dead-end filtration system has a second plurality of hollow fiber membranes and configured to dead-end filter the additional algae received from the second cultivation stage so as to produce a second permeate and a second retentate.
  • the algae harvesting and cultivation system is further constructed and arranged such that the second permeate flows back to the second cultivation stage.
  • an algae harvesting and cultivation system includes (i) an algae cultivator having at least one cultivation device having a cultivation media for growing algae to produce an algae slurry, and (ii) at least one treatment tank defining a plurality of filtration stages including at least a first filtration stage and a second filtration stage, wherein the first filtration stage is in fluid communication with the algae cultivator such that the first filtration stage receives the algae slurry.
  • the first filtration stage includes (a) a first at least one membrane filtration module positioned inside the treatment tank, wherein the first membrane filtration module includes a first plurality of hollow fiber membranes having a first total outside filtration area and defining lumens, (b) a retentate outlet, and (c) a permeate outlet.
  • the second filtration stage includes (a) a second at least one membrane filtration module positioned inside the treatment tank, wherein the second membrane filtration module includes a second plurality of hollow fiber membranes having a second total outside filtration area and defining lumens, (b) an inlet coupled fluidly to the retentate outlet of the first filtration stage, (c) a retentate outlet, and (d) a permeate outlet.
  • the algae harvesting and cultivation system is configured to cultivate algae and perform dead-end filtration of the algae slurry by allowing the algae slurry to flow from the algae cultivator to the first filtration stage, pulling permeate through pores of the first hollow fiber membranes at a first flux so that a first retentate is produced outside the lumens of the first hollow fiber membranes, allowing at least a portion of the first retentate to flow from the first filtration stage retentate outlet to the second filtration stage retentate inlet, and pulling permeate through pores of the second hollow fiber membranes at a second flux so that a second retentate is produced outside the lumens of the second plurality of hollow fiber membranes, and) allowing the permeate from the first and second filtration stages to flow back to the algae cultivator for use in the cultivation media for growing algae.
  • an algae harvesting system provides (i) at least one treatment tank having a rinse fluid inlet and (ii) a retentate outlet, (iii) at least one membrane filtration module positioned inside the treatment tank, wherein the membrane filtration module includes a plurality of hollow fiber membranes defining lumens; (iv) a source of algae slurry in a media, the source of algae slurry coupled fluidly to the at least one treatment tank such that the at least one treatment tank can receive the algae slurry; (v) a source of rinse fluid, the source of rinse fluid coupled fluidly to the rinse fluid inlet of the at least one treatment tank such that the at least one treatment tank can receive the rinse fluid; and (vi) a media sensor configured to sense the concentration of media in the algae slurry.
  • the system is configured to (a) perform dead-end filtration of the algae slurry received in the treatment tank by pulling a substantially algae-free permeate through pores of the hollow fiber membranes so that the permeate flows inside the lumens of the hollow fiber membranes and a retentate of the algae slurry is produced outside the lumens of the hollow fiber membranes, (b) perform a backwash sequence in which a backwash liquid flows inside the lumens of the hollow fiber membranes and is pushed through the pores of the hollow fiber membranes to remove any foulants that have accumulated on the plurality of hollow fiber membranes, and (c) perform a rinse sequence in which (i) the treatment tank stops receiving the algae slurry from the source of algae slurry, and (ii) the treatment tank receives the rinse fluid from the source of rinse fluid through the rinse fluid inlet until the at least one media sensor senses that at least ninety percent of the media has been replaced with the rinse fluid.
  • an algae harvesting system provides at least one treatment tank defining a plurality of filtration stages including at least a first filtration stage and a second filtration stage.
  • the first filtration stage includes (i) a first at least one membrane filtration module positioned inside the at treatment tank, wherein the first membrane filtration module includes a first plurality of hollow fiber membranes having a first total outside filtration area and defining lumens, (ii) a retentate outlet, and (iii) a permeate outlet.
  • the second filtration stage includes (i) a second at least one membrane filtration module positioned inside the treatment tank, wherein the second membrane filtration module includes a second plurality of hollow fiber membranes having a second total outside filtration area and defining lumens, (ii) a retentate inlet coupled fluidly to the retentate outlet of the first filtration stage, (ii) a rinse fluid inlet, (iii) a retentate outlet, and (iv) a permeate outlet.
  • the algae harvesting system further provides a media sensor configured to sense a concentration of media in an algae slurry in the at least one treatment tank.
  • the system is configured to perform dead-end filtration of the algae slurry contained in the treatment tank by (i) pulling permeate through pores of the first hollow fiber membranes at a first flux so that the permeate flows inside the lumens of the first hollow fiber membranes and a first retentate is produced outside the lumens of the first hollow fiber membranes, (ii) allowing at least a portion of the first retentate to flow through the retentate outlet of the first filtration stage to the inlet of the second filtration stage, and (iii) pulling permeate through pores of the second hollow fiber membranes at a second flux so that the permeate flows inside the lumens of the second hollow fiber membranes and a second retentate is produced outside the lumens of the second hollow fiber membranes.
  • the system is further configured to perform a backwash sequence in which a backwash liquid flows (i) inside the lumens of the first plurality of hollow fiber membranes and is pushed through the pores of the first plurality of hollow fiber membranes to remove any foulants that have accumulated on the first plurality of hollow fiber membranes, and (ii) inside the lumens of the second plurality of hollow fiber membranes and is pushed through the pores of the second plurality of hollow fiber membranes to remove any foulants that have accumulated on the second plurality of hollow fiber membranes.
  • a backwash liquid flows (i) inside the lumens of the first plurality of hollow fiber membranes and is pushed through the pores of the first plurality of hollow fiber membranes to remove any foulants that have accumulated on the first plurality of hollow fiber membranes, and (ii) inside the lumens of the second plurality of hollow fiber membranes and is pushed through the pores of the second plurality of hollow fiber membranes to remove any foulants that have accumulated on the second plurality of hollow fiber membranes.
  • the system is additionally configured to perform a rinse sequence in which (i) the first retentate stops flowing from the first filtration stage to the second filtration stage, and (ii) the rinse fluid flows to the second filtration stage through the rinse fluid inlet until the media sensor senses that that at least ninety percent of the media has been replaced with the rinse fluid.
  • an algae harvesting and cultivation system provides (a) an algae cultivator including at least one cultivation device having a cultivation media for growing algae to produce an algae slurry, and (b) at least one treatment tank defining a plurality of filtration stages including at least a first filtration stage and a second filtration stage, wherein the first filtration stage is in fluid communication with the algae cultivator such that the first filtration stage receives the algae slurry.
  • the first filtration stage includes (i) a first at least one membrane filtration module positioned inside the treatment tank, wherein the first membrane filtration module includes a first plurality of hollow fiber membranes having a first total outside filtration area and defining lumens, (ii) a retentate outlet, and (iii) a permeate outlet.
  • the second filtration stage includes (i) a second at least one membrane filtration module positioned inside the treatment tank, wherein the second membrane filtration module includes a second plurality of hollow fiber membranes having a second total outside filtration area and defining lumens, (ii) an inlet coupled fluidly to the retentate outlet of the first filtration stage, (iii) a retentate outlet, and (iv) a permeate outlet.
  • the algae harvesting and cultivation system further provides a live algae container coupled fluidly to the second filtration stage to receive the second retentate.
  • the system is configured to cultivate algae and perform dead-end filtration of the algae slurry by: (i) allowing the algae slurry to flow from the algae cultivator to the first filtration stage, (ii) pulling permeate through pores of the first plurality of hollow fiber membranes at a first flux so that a first retentate is produced outside the lumens of the first plurality of hollow fiber membranes, (iii) allowing at least a portion of the first retentate to flow from the first filtration stage retentate outlet to the second filtration stage retentate inlet, (iv) pulling permeate through pores of the second plurality of hollow fiber membranes at a second flux so that a second retentate is produced outside the lumens of the second plurality of hollow fiber membranes, (v) allowing the permeate from the first and second filtration stages to flow back to the algae cultivator for use in the cultivation media for growing algae, and (vii) flowing live algae in the second retentate from the second filtration stage to the live
  • One advantage of the present disclosure is to provide algae harvesting systems and methods that reduce backwashing periods and/or intervals while producing high concentrations of algae product.
  • Yet another advantage of the present disclosure is to provide multistage hollow fiber dead-end filtration systems having variable flux in each stage (and in certain embodiments decreasing area in each stage) to increase the average flux per module.
  • an advantage of the present disclosure is to provide shorter valve opening and/or closing times, thereby increasing the overall system flux and enabling shorter backwash periods and/or intervals.
  • a further advantage of the present disclosure is to produce concentrated algae slurries by harvesting and dewatering the algae in dead-end filtration systems and then re cultivating by dilution with the same growth media or a different growth media and the live algae slurries can be stored before re-cultivation.
  • Another advantage of the present disclosure therefore is that live algae slurries can be used to retain a concentrated inoculum for recovery from system upsets the concentrated slurries represent and the concentrated algae slurries produced by harvesting and dewatering in dead-end filtration systems slurries can be stored and re-cultivated and a 50 to 400-fold reduction in volume is achieved relative to the cultivation system thereby enabling concentrated algae slurries to be efficiently shipped to another location.
  • An advantage of the present disclosure is therefore to utilize hollow fiber dead-end filtration systems and methods to produce concentrated live algae slurries that can be stored for use at a later time, and to utilize hollow fiber dead-end filtration to produce concentrated live algae slurries that can be shipped for use at another location.
  • a further advantage of the present disclosure is to provide hollow fiber dead-end filtration systems and methods for algae harvesting that reduce energy use so that inclusion of rinses and media adjustments at an intermediate or final filtration stage results in minimal energy penalty, and to recover most or all of the dissolved solids in a permeate flow during algae harvesting and dewatering with hollow fiber dead-end filtration.
  • FIG. 1 is a schematic diagram illustrating an embodiment of a hollow fiber dead-end filtration system of the present disclosure having a single permeate pump.
  • FIG. 2 is a schematic diagram illustrating an embodiment of a hollow fiber dead-end filtration system of the present disclosure having a reversible permeate flow and backwash pump.
  • FIG. 3 is a schematic diagram illustrating a typical hollow fiber dead-end filtration system of the present disclosure having separate permeate and backwash pumps.
  • Fig. 4 is a schematic diagram illustrating an embodiment of a hollow fiber dead-end filtration system of the present disclosure having a permeate pump and a gravity fed backwash.
  • Fig. 5 is a schematic diagram illustrating an embodiment of a hollow fiber dead-end filtration system of the present disclosure having permeate siphoning and gravity fed backwash.
  • FIG. 6 is a schematic diagram illustrating an embodiment of a multistage hollow fiber dead-end filtration system of the present disclosure having gravity backwash and permeate siphoning.
  • FIG. 7 is a schematic diagram illustrating an embodiment of a multistage hollow fiber dead-end filtration system of the present disclosure having gravity backwash, permeate siphoning, and a transfer tank.
  • FIG. 8 illustrates an embodiment of a treatment tank for a hollow fiber dead-end filtration system of the present disclosure in which the treatment tank has generally vertical side walls.
  • FIG. 9 illustrates another embodiment of a treatment tank for a hollow fiber dead end filtration system of the present disclosure in which the treatment tank is an earthen lined tank or pond having angled side walls.
  • Fig. 10 is a schematic diagram illustrating an embodiment of an algae harvesting and cultivation system of the present disclosure in which carbon dioxide can be added, permeate can be re-used for cultivation, and live algae retentate can be attained.
  • Fig. 11 is a flow chart illustrating an embodiment of utilizing a carbonate- bicarbonate shuttle for a carbon dioxide cycle in the system of Fig. 10.
  • Fig. 12 is a schematic diagram illustrating an embodiment of a harvesting and cultivation system of the present disclosure having dead-end filtration and in which the media is recharged with carbon dioxide through an absorber prior to recycling the media to an algae cultivator.
  • Fig. 13 is a schematic diagram illustrating an embodiment of a multi- or two-stage cultivation and harvesting system of the present disclosure having separate media in each cultivation stage.
  • Fig. 14 is a flow chart illustrating an embodiment of a multi- or two-stage cultivation and harvesting system and method of the present disclosure that incorporates hollow fiber dead-end filtering, rinsing, second stage pre-treating as well as recycling and recovering of separate media for each stage.
  • Fig. 15 is a schematic diagram illustrating an embodiment of a multi- or two-stage cultivation and harvesting system of the present disclosure having dead-end filtration and in which carbon dioxide can be added and separate media can be used in each cultivation stage.
  • Fig. 16 is a schematic diagram illustrating an embodiment of a filtration system of the present disclosure in which multiple modules are connected or coupled fluidly in parallel within a cassette, and in which backwash, filtration and other systems operations can be performed through a single set of valves.
  • Fig. 17 is a schematic diagram illustrating an embodiment of a hollow fiber dead-end filtration system of the present disclosure in which multiple cassettes having modules are connected or coupled fluidly in parallel within a bank, and in which backwash, filtration and other system operations can be performed through a single set of valves.
  • Fig. 18 is a schematic of diagram illustrating an embodiment of a hollow fiber dead end filtration system of the present disclosure having a single permeate pump with added pressure control elements.
  • Fig. 19 is a schematic of diagram illustrating an embodiment of a hollow fiber dead end filtration system of the present disclosure having an air-actuated diaphragm permeate pump and an elevated backwash tank.
  • FIG. 20 is a schematic of diagram illustrating an embodiment of a hollow fiber dead end filtration system of the present disclosure having a separate permeate pump and backwash pumps with added pressure control elements.
  • Fig. 21 is a schematic of diagram illustrating an embodiment of a hollow fiber dead end filtration system of the present disclosure having a separate permeate pump and backwash pumps with a stand-pipe for backwash pressure control.
  • Fig. 22 is a schematic of diagram illustrating an embodiment of a hollow fiber dead end filtration system of the present disclosure having a permeate pump and a gravity fed backwash with added pressure control elements.
  • FIG. 23 is a schematic of diagram illustrating an embodiment of a hollow fiber dead end filtration system of the present disclosure having a permeate pump and an air-bladder fed backwash.
  • Fig. 24 is a schematic of diagram illustrating an embodiment of a hollow fiber dead end filtration system of the present disclosure having permeate siphoning and a gravity fed backwash with pressure control loops.
  • Fig. 25 is a schematic of diagram illustrating an embodiment of a hollow fiber dead end filtration system of the present disclosure having permeate siphoning and an air-bladder fed backwash.
  • Fig. 26 is a schematic of diagram illustrating an embodiment of a multistage hollow fiber dead-end filtration system of the present disclosure having gravity backwash and permeate siphoning with independent pressure or flow control for each stage.
  • Fig. 1 illustrates one non-limiting embodiment of a hollow-fiber dead-end filtration system of the present disclosure.
  • the system includes a treatment tank 10 structured and arranged to receive and treat a liquid feed containing suspended solids (e.g., a biological slurry or algae slurry/feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve) to produce a filtered permeate substantially free of suspended solids and a retentate with a higher suspended solids content than the liquid feed.
  • a plurality of submerged hollow fiber membranes 12 are contained or positioned within treatment tank 10.
  • the submerged hollow fiber membranes 12 can be arranged into one or more module 11 that is contained, supported or held in treatment tank 10.
  • the outer surface of the hollow fiber membranes 12 is in contact with the liquid feed and retentate.
  • the one or more module 11 can also be arranged into one or more cassette.
  • the one or more module 11 in the illustrated embodiment can include headers attached to each hollow fiber membrane 12 so as to create a watertight connection between the outside of the membranes 12 and a permeate channel in the header.
  • permeate is pumped or pulled through pores of the hollow fiber membranes so that permeate is withdrawn through the inside of the lumens of the hollow fiber membranes and retentate is produced outside the lumens of the hollow fiber membranes (e.g., inside the treatment tank).
  • a blower 13 can push air through a conduit and a distributer 14 to create air bubbles 15 that are released below the hollow fibers to create fluid movement and movement of the hollow fibers, which aids in reducing fouling and improving backwash efficiency.
  • the air bubbles can be released continuously, intermittently, or only during the backwash cycles.
  • valves 21 and 23 are open, valves 25 and 26 are closed, and permeate is withdrawn through at least one conduit via pump 22.
  • Valve 24 is opened and valve 23 is closed intermittently to maintain the fluid level in a permeate holding tank 20.
  • a controller 29 e.g., a programmable logic controller controls permeate pump 22 based upon the permeate flow rate measured by flow meter 28 and the suction or negative pressure measured via pressure transducer 27.
  • a backwashing sequence is initiated by opening valve 25, closing valve 21, closing valves 24 and 23, and opening valve 26.
  • Permeate pump 22 pumps permeate from permeate holding tank 20 through at least one conduit to the inside of the lumens defined by hollow fiber membranes 12 of module 11.
  • Controller 29 e.g., a programmable logic controller
  • Controller 29 controls the flow rate of pump 22 to maintain a desired backwash pressure, as measured by pressure transducer 27.
  • withdrawal of the permeate is resumed by opening valves 21 and 23, and closing valves 25 and 26.
  • multiple modules 11 can be connected in parallel in a cassette so that the entire cassette can be backwashed at the same time.
  • Certain embodiments can also include multiple cassettes connected in parallel in a bank so that the multiple cassettes can be backwashed at the same time.
  • the backwash off-line period includes the time between stopping permeate flow from module 11 and restarting permeate flow from module 11.
  • the backwash off-line period includes one or more of: (i) the time to open and close valves 21, 23, 24, 25, and 26 for backwash; (ii) the time to reach the backwash pressure; (iii) the time for the backwash flow, (iv) the time to open and close valves 21, 23, 24, 25, and 26 for permeate flow; (v) the time to lower the pressure in the permeate lines to resume the permeate flow.
  • the backwash off-line period for the system of Fig. 1 includes the time for each of (i) to (v) above.
  • the backwash interval in an embodiment includes the time between the start of one backwash cycle and the start of a next backwash cycle.
  • controller 29 can in various embodiments include one or more controller, which can be programmed or configured to operate with one or more of the valves, the blower, the pressure transducer, the flow meter, the pump, any sensors and/or any other system components so as to perform various functions of the system including valving, pumping, backwashing, rinsing, filtration, permeate flow, chemical cleaning or any other system functions.
  • the one or more controller can include at least one processor and at least one memory device which stores instructions, which when executed by the at least one processor, cause the at least one processor to operate with one or more of the valves, the blower, the pressure transducer, the flow meter, any sensors, and/or the pump to perform operations of the filtration system.
  • the Fig. 1 system can include at least one input device and/or at least one display device, and the one or more controller can be programmed or configured to operate with the at least at least one input device and/or at least one display device.
  • Fig. 2 illustrates another non-limiting embodiment of a hollow-fiber dead-end filtration system of the present disclosure.
  • the system of Fig. 2 includes many of the same components described above in connection with Fig. 1. Those components in Fig. 2 are marked with the same or similar element numbers as used in Fig. 1. The description of those elements including each of the alternatives discussed above in connection with Figs. 1 and 2 apply in many respect to like element numbers in Fig 2.
  • Pump 22 in the system of Fig. 2 is a reversible pump that performs filtration or permeate flow as well as backwash flow.
  • a treatment tank 10 structured and arranged to receive and treat a liquid feed containing suspended solids (e.g., a biological slurry or algae slurry/feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve) to produce filtered permeate substantially free of suspended solids and a retentate with a suspended solids content higher than the liquid feed.
  • a plurality of submerged hollow fiber membranes 12 are contained or held within treatment tank 10.
  • the submerged hollow fiber membranes 12 can be arranged into one or more module 11 that is contained in treatment tank 10.
  • the one or more module 11 can also be arranged into one or more cassette.
  • the hollow fiber membrane module 11 can include headers attached to each hollow fiber membrane 12 so as to create a watertight connection between the outside of the membranes 12 and a permeate channel of the header.
  • the outer surface of the hollow fiber membranes 12 is in contact with the liquid feed and retentate.
  • a blower IB can push air through at least one conduit and distributer 14 to create air bubbles 15 that are released below the hollow fibers to create fluid movement and movement of the hollow fibers, which aids in reducing fouling and improving backwash efficiency.
  • the air bubbles can be released continuously, intermittently, or only during the backwash cycles.
  • permeate is withdrawn from the lumens of the hollow fiber membranes through at least one conduit via permeate pump 22, valve 24 is opened and valve 23 is closed intermittently to maintain the fluid level in permeate holding tank 20.
  • a controller 29 e.g., a programmable logic controller
  • a backwashing sequence is initiated by opening valve 24, closing valve 23, and reversing the flow in pump 22 so that permeate can be withdrawn from permeate holding tank 20 (through the same at least one conduit as the conduit for filtration) and the retentate is pushed through the pores of the hollow fiber membranes into treatment tank 10.
  • the flow rate of pump 22 is controlled by at least one controller 29 (e.g., a programmable logic controller) to maintain the desired backwash pressure as measured by pressure transducer 27.
  • multiple modules 11 can be connected in parallel in a cassette so that the entire cassette can be backwashed at the same time.
  • Certain embodiments can also include multiple cassettes connected in parallel in a bank so that the multiple cassettes can be backwashed at the same time.
  • the backwash off-line period includes the time between stopping permeate flow from module 11 and restarting permeate flow from module 11.
  • the backwash off-line period includes one or more of: (i) the time to ramp pump 22 down and accelerate the pump in the opposite flow direction for backwash flow; (ii) the time to reach the backwash pressure; (iii) the time for the backwash flow; (iv) the time to ramp pump 22 down and accelerate the pump 22 in the opposite flow direction for permeate flow; and (v) the time to lower the pressure in the permeate lines to resume the permeate flow.
  • the backwash off-line period includes the time for each of (i) to (v) above.
  • the backwash interval in an embodiment includes the time between the start of one backwash cycle and the start of the next backwash cycle.
  • controller 29 in the system of Fig. 2 can in various embodiments include one or more controller, which can be programmed or configured to operate with one or more of the valves, the blower, the pressure transducer, the flow meter, the pump, any sensors and/or any other system components so as to perform various functions of the system including valving, pumping, backwashing, rinsing, filtration, permeate flow, chemical cleaning or any other system functions.
  • the one or more controller can include at least one processor and at least one memory device which stores instructions, which when executed by the at least one processor, cause the at least one processor to operate with one or more of the valves, the pressure transducer, the flow meter, any sensors, and the pump to perform operations of the filtration system.
  • the Fig. 2 system can include at least one input device and/or at least one display device, and the one or more controller can be programmed or configured to operate with the at least at least one input device and/or at least one display device.
  • FIG. 3 an additional non-limiting embodiment of a hollow-fiber dead-end filtration system of the present disclosure is illustrated in which separate permeate and backwash pumps are utilized.
  • the system of Fig. 3 includes many of the same components described above in connection with Figs. 1 and 2. Those components in Fig. 3 are marked with the same or similar element numbers as used in Figs. 1 and 2. The description of those elements including each of the alternatives discussed above in connection with Figs. 1 and 2 apply in many respects to like element numbers in Fig. 3.
  • the system of Fig. 3 includes many of the same components described above in connection with Figs. 1 and 2. Those components in Fig. 3 are marked with the same or similar element numbers as used in Figs. 1 and 2. The description of those elements including each of the alternatives discussed above in connection with Figs. 1 and 2 apply in many respects to like element numbers in Fig. 3.
  • the system of Fig. 3 includes many of the same components described above in connection with Figs. 1 and 2. Those components in Fig.
  • a treatment tank 10 structured and arranged to receive and treat a liquid feed containing suspended solids (e.g., an algae feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve) to produce filtered permeate substantially free of suspended solids and retentate with a higher suspended solids content than the liquid feed.
  • the treatment tank 10 contains submerged hollow fiber membranes 12 arranged into one or more module 11.
  • the one or more module 11 can also be arranged into one or more cassette.
  • the one or more module 11 in an embodiment includes headers attached to the hollow fiber membranes 12 to create a watertight connection between the outside of the membranes 12 and a permeate channel of the header.
  • the outer surface of the hollow fiber membranes 12 is in contact with the liquid feed and retentate.
  • the permeate is pulled or pumped through pores of the hollow fiber membranes 12 so that the permeate is withdrawn through the inside of the lumens of the hollow fibers and retentate is produced outside the lumens of the hollow fibers (e.g., inside the treatment tank).
  • valves 21 and 23 are open, valve 25 is closed, and permeate is withdrawn through at least one conduit by pump 22.
  • Valve 24 is opened and valve 23 is closed intermittently to maintain the fluid level in the permeate holding tank 20.
  • the permeate pump 22 is controlled by one or more controller 29 (e.g., a programmable logic controller) based upon the permeate flow rate measured by flow meter 28 and the suction pressure measured by the pressure transducer 27.
  • a backwash sequence is initiated by closing valve 21, stopping pump 22, opening valve 25 and starting pump 30 so that backwash or permeate fluid flows through at least one conduit to module 11.
  • the flow rate of pump 30 is controlled by a controller 73 (e.g., a programmable logic controller) to maintain the desired backwash pressure as measured by pressure transducer 27.
  • the flow rate of pump 30 can additionally or alternatively be controlled by the same controller that controls permeate pump 22.
  • withdrawal of permeate is resumed by stopping pump 30, closing valve 25, opening valve 21, and starting pump 22.
  • multiple modules 11 can be connected in parallel in a cassette so that the entire cassette can be backwashed at the same time.
  • Certain embodiments can also include multiple cassettes connected in parallel in a bank so that the multiple cassettes can be backwashed at the same time.
  • the backwash off-line period includes the time between stopping permeate flow from module 11 and restarting permeate flow from module.
  • the backwash off-line period includes one or more of: (i) the time to open and close valves 21 and 25 for backwash flow; (ii) the time to ramp up pump 30; (iii) the time for the backwash flow; (iv) the time to ramp down pump 30, (v) the time open and close valves 21 and 25 to resume permeate flow for filtration; and (vi) the time to ramp up pump 22 to lower the pressure in the permeate lines to resume the permeate flow.
  • the backwash off-line period for the system of Fig. 3 includes each of (i) to (vi) above.
  • the backwash interval in an embodiment includes the time between the start of one backwash cycle and the start of the next backwash cycle.
  • controllers 29, 73 in the system of Fig. 3 can in various embodiments include one controller alone or multiple controllers including more than two controllers. Either the single controller or multiple controllers can be programmed or configured to operate with one or more of the valves, the pressure transducer, the flow meter, the pumps, any sensors and/or any other system components so as to perform various functions of the system including valving, pumping, backwashing, rinsing, permeate flow, chemical cleaning or any other system functions.
  • the one or more controller can include at least one processor and at least one memory device which stores instructions, which when executed by the at least one processor, cause the at least one processor to operate with one or more of the valves, the pressure transducer, the flow meter, any sensors, and pumps to perform system operations. It should additionally be appreciated that certain embodiments of the Fig. 3 system can include at least one input device and/or at least one display device, and the one or more controller can be programmed or configured to operate with the at least at least one input device and/or at least one display device.
  • FIG. 4 another non-limiting hollow fiber membrane filtration system of the present disclosure is illustrated in which backwash is performed via gravity.
  • the system of Fig. 4 also includes many of the same components described above in connection with Figs. 1 to 3. Those components in Fig. 4 are marked with the same or similar element numbers as used in Figs. 1 to 3. The description of those elements including each of the alternatives discussed above in connection with Figs. 1 to 3 apply in many respects to like element numbers in Fig. 3.
  • a treatment tank 10 structured and arranged to receive and treat a liquid feed containing suspended solids (e.g., an algae feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve) to produce a filtered permeate substantially free of suspended solids and a retentate with a higher suspended solids content than the liquid feed.
  • the treatment tank 10 contains submerged hollow fiber membranes 12 arranged into one or more module 11, which can be arranged into one or more cassette. In the illustrated embodiment, the submerged hollow fiber membranes 12 are arranged into a single module 11 that is contained in treatment tank 10.
  • one or more module 11 can include headers attached to each hollow fiber membrane 12 to create a watertight connection between the outside of the membranes 12 and a permeate channel of the header.
  • the outer surface of the hollow fiber membranes is in contact with the liquid feed and retentate.
  • permeate is pumped or pulled through pores of the hollow fiber membranes so that the permeate is withdrawn through the inside of the lumens of the hollow fibers and a retentate is produced outside the lumens of the hollows fibers of the membrane.
  • valves 21 and 23 are open, valve 25 is closed, and permeate is withdrawn through at least one conduit by pump 22.
  • Valve 24 is opened and valve 23 is closed intermittently to maintain the fluid level in an elevated permeate gravity feed tank 40.
  • At least one controller 29 e.g., a programmable logic controller controls permeate pump 22 based upon the permeate flow rate measured by flow meter 28.
  • a backwashing sequence is initiated by closing valve 21, stopping pump 22, and opening valve 25 so that backwash or permeate fluid can flow through at least one conduit to module 11.
  • the backwash pressure is controlled by a difference in height between the permeate gravity feed tank 40 and the liquid level in treatment tank 10. Once the backwash flow time is complete, withdrawal of permeate is resumed by closing valve 25, opening valve 21, and starting pump 22.
  • multiple modules 11 can be connected in parallel in a cassette so that the entire cassette can be backwashed at the same time.
  • Certain embodiments can also include multiple cassettes connected in parallel in a bank so that the multiple cassettes can be backwashed at the same time.
  • the backwash off-line period includes the time between stopping permeate flow from module 11 and restarting permeate flow from module 11.
  • the backwash off-line period includes one or more of: (i) the time to open and close valves 21 and 25 to stop permeate flow from module 11 and to start backwash flow to module 11; (ii) the time for the backwash flow; (iii) the time open and close valves 21 and 25 to stop backwash flow and resume permeate flow for filtration; and (iv) the time to ramp up pump 22 to lower the pressure in the permeate lines to resume the permeate flow.
  • the backwash off-line period includes the time for each of (i) to (iv) above.
  • the backwash interval in an embodiment includes the time between the start of one backwash cycle and the start of the next backwash cycle.
  • controller 29 in the system of Fig. 4 can in various embodiments include one or more controller, which can be programmed or configured to operate with one or more of the valves, the flow meter, the pump, any sensors, and/or any other system components so as to perform various functions of the system including valving, pumping, backwashing, rinsing, filtration, permeate flow, chemical cleaning or any other system functions.
  • the one or more controller can include at least one processor and at least one memory device which stores instructions, which when executed by the at least one processor, cause the at least one processor to operate with one or more of the valves, the flow meter, any sensors, and the pump to perform operations of the filtration system.
  • certain embodiments of the Fig. 4 system can include at least one input device and/or at least one display device, and the one or more controller can be programmed or configured to operate with the at least at least one input device and/or at least one display device.
  • FIG. 5 another non-limiting embodiment of a hollow fiber filtration system is illustrated in which backwash is performed via gravity and siphoning or a siphoning system is used to pull the permeate for filtration.
  • Pumps are typically used in hollow fiber membrane filtration systems to reduce pressure in the permeate lines so that the permeate inside the lines can be pulled through the hollow-fibers of the membranes.
  • Gravity driven siphon systems according to the present disclosure (e.g., Figs. 5, 6 and 7) eliminate the need for such a pump and instead pull permeate via siphoning through hollow fiber membranes in a dead-end filtration operation.
  • the siphoning feature or systems of the present disclosure utilize the fact that pressure lower than atmospheric pressure allows fluid to be pulled through the hollow fiber membranes.
  • air can enter the system in various ways. For example, air can enter from leaks, from air bubbles being pulled through the hollow-fiber membrane to reduce fouling, or from dissolution of air in the permeate system as a result of the permeate being saturated at atmospheric pressure and the pressure in the siphon lines being less than atmospheric pressure.
  • the effectiveness of siphoning or siphon systems can be reduced by air accumulation in the siphon lines.
  • the diameter of the siphon lines can therefore be selected so that flux is high enough to pull the air through the line.
  • a high point located in the siphon line can be used to collect the air and a vacuum pump can be used to remove the air.
  • An additional pump and gas level monitoring and vacuum pump controls can be necessary with this approach to ensure that permeate does not enter the vacuum pump.
  • the system of Fig. 5 includes many of the same components described above in connection with Figs. 1 to 4. Those components in Fig. 5 are marked with the same or similar element numbers as used in Figs. 1 to 4. The description of those elements including each of the alternatives discussed above in connection with Figs. 1 to 4 apply in many respects to like element numbers in Fig. 5.
  • treatment tank 10 structured and arranged to receive and treat a liquid feed containing suspended solids (e.g., an algae feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve 19) to produce a filtered permeate substantially free of suspended solids and a retentate with a higher suspended solids content than the liquid feed.
  • Treatment tank 10 contains submerged hollow fiber membranes 12 arranged into one or more modules 11, which can be arranged into one or more cassette. In the illustrated embodiment, the submerged hollow fiber membranes 12 are arranged into a single module that is contained in treatment tank 10.
  • the one or more modules 11 can include headers attached to each hollow fiber membrane 12 so as to create a watertight connection between the outside of the membranes 12 and a permeate channel of the header.
  • the outer surface of the hollow fiber membranes is in contact with the liquid feed and retentate.
  • permeate is withdrawn or pulled through pores of the hollow fiber membranes so that the permeate is withdrawn through the inside of the lumens of the hollow fibers and a retentate is produced outside the lumens of the hollow fibers.
  • the liquid level in treatment tank 10 is controlled by intermittent opening of the feed valve 19.
  • valves 21 and 23 are open, valves 25 and 26 are closed, and permeate is pulled or withdrawn by siphon through at least one permeate or siphon conduit 36 into the permeate siphon tank 41.
  • the suction pressure of the siphon is controlled by the difference in height between the liquid in treatment tank 10 and permeate level in permeate siphon tank 41.
  • Pump 42 can be operated intermittently to maintain the level in siphon tank 41.
  • Valve 24 can be opened and valve 23 can be closed intermittently to maintain the fluid level in elevated permeate gravity feed tank 40. It should be appreciated that in various embodiments, the suction, pulling or siphon process of permeate withdrawal can begin, for example, by bleeding air from the fluid conduit or line on which valve 21 operates (e.g., conduit 36) and/or by adding a liquid such as water into that same conduit.
  • the process of permeate withdrawal can being, for example, via bleeding air from the lines or conduits in which one or more of valves 25 operate (e.g., valves 25a, 25b, or 25c discussed below) and/or by adding a liquid such as water into the same lines or conduits.
  • valves 25 e.g., valves 25a, 25b, or 25c discussed below
  • at least one liquid level sensor can be included in tank 10 to sense and control the level of liquid in treatment tank 10.
  • a backwash sequence in the system of Fig. 5 can be initiated by (i) closing valve 21 and opening valve 25 so that backwash or permeate fluid can flow through at least one conduit to module 11, and (ii) controlling the backwash pressure by a difference in height between the permeate gravity feed tank 40 and the liquid level in treatment tank 10.
  • a purge valve 26 can be coupled to a purge conduit 47 at a high point in the permeate or siphon conduit 36 where gas can accumulate.
  • a purge valve 26 can be opened to purge any gas that has accumulated in the siphon or permeate conduit 36.
  • Gas discharge line or conduit 47 is much smaller in diameter than permeate or siphon line 36, so that when purge valve 26 is opened there is only a small reduction in backwash flow while the gas is being purged. Purge valve 26 is closed before or when the backwash flow time is complete. Once the backwash flow time is complete, withdrawal of permeate is resumed closing valves 25 and 26 and opening valve 21. It should be appreciated that multiple purge conduits 47 and valves 26 could be utilized instead of a single purge conduit. It should also be appreciated that one or more purge conduits can be coupled to the at least one permeate conduits in any of the multi stage harvesting systems described herein.
  • the backwash off-line period includes the time between stopping permeate flow from module 11 and restarting permeate flow from module 11.
  • the backwash off-line period includes one or more of: (i) the time to open and close valves 21 and 25 to stop permeate flow from module 11 and to start backwash flow to module 11; (ii) the time for the backwash flow; and (iii) the time to open and close valves 21 and 25 to stop backwash flow and resume permeate flow for filtration.
  • the backwash off line period includes the time for each of (i) to (iii) above.
  • the backwash interval in an embodiment includes the time between the start of one backwash cycle and the start of the next backwash cycle. It should be appreciated that in certain embodiments, multiple modules 11 can connected in parallel in a cassette so that the entire cassette can be backwashed at the same time. Certain embodiments can also include multiple cassettes connected in parallel in a bank so that the multiple cassettes can be backwashed at the same time.
  • treatment tank 10 can be emptied, and optionally rinsed. To empty the tank, filtration can be stopped by closing valves 25, 21 and 19. The treatment tank 10 can then be emptied via operation of pump 16. After treatment tank 10 is emptied, a rinse can optionally be performed prior to restarting the filtration process for tank 10. To perform a rinse, treatment tank 10 is filled with water or a suitable cleaning solution, and cleaning valve 72 is opened so that water or a cleaning solution can be added to tank 10 (e.g., water or cleaning solution held in a rinsing solution source or container flowing through a conduit coupled to the source and to tank 10).
  • water or a cleaning solution can be added to tank 10 (e.g., water or cleaning solution held in a rinsing solution source or container flowing through a conduit coupled to the source and to tank 10).
  • the rinse water or cleaning solution can be removed from treatment tank 10 via operation of pump 16.
  • the water used for the rinse can also contain cleaning chemicals to aid in rinsing the tank or cleaning the membranes.
  • the water or solution can be emptied from treatment tank through one or more outlet or conduit via operation of pump 16 (and opening a valve on the conduit in some embodiments), after which valve 19 can be opened so as to refill treatment tank 10 with in-feed and the system can utilize valves 25 and 21 to perform filtration and backwash with no retentate discharge until the desired solid concentration level is attained again. This cycle of emptying the retentate and optionally rinsing the treatment tank 10 can be repeated one or more times.
  • one or more algae concentration sensor can again be utilized to determine when the desired solid algae concentration has been reached.
  • Such one or more sensor can be located, for example, in treatment tank 10 or in any other suitable location.
  • the system can be configured to determine the solid concentration level attainment based upon volumetric control, which can utilize, for example, a flow meter or any known flow and/or volumetric parameters.
  • feed valve 19 can be closed and the liquid level in treatment tank 10 can be controlled by intermittent opening of valve 72 to add water or any other suitable replacement solution to replace the original media of the algae slurry.
  • the water or replacement solution entering treatment tank 10 dilutes the original media and eventually replaces at least most of the media.
  • the media replacement level can be monitored, sensed or determined by any suitable sensor or sensing methods such as (i) sensing or determining the difference in conductivity, pH, ion specific electrode, or specific gravity of the algae slurry retentate or permeate relative to the initial value of the of the in the algae slurry retentate or permeate, or (ii) sensing or determining the level of media replacement through total volumetric throughput of rinse water or solution, measured, for example, by a rinse feed flow meter or permeate flow meter, relative to the total volume of treatment tank 10.
  • the rinsed algae slurry retentate can be removed from treatment tank 10 through an outlet or conduit via operation of pump 16 (and in some embodiments via operation of a valve on the conduit with which pump 16 operates).
  • the system of Fig. 5 can in various embodiments include one or more controller, which can be programmed or configured to operate with one or more of the valves, the pump, any sensors and/or any other system components so as to perform various functions of the system including valving, pumping, backwashing, rinsing, filtration, permeate flow, chemical cleaning or any other system functions.
  • the one or more controller can include at least one processor and at least one memory device which stores instructions, which when executed by the at least one processor, cause the at least one processor to operate with one or more of the valves, the pump, and sensors or any other components to perform operations of the filtration system.
  • certain embodiments of the Fig. 5 system can include at least one input device and/or at least one display device, and the one or more controller can be programmed or configured to operate with the at least at least one input device and/or at least one display device.
  • each of the filtration systems illustrated in the embodiments of Figs. 1 to 5 can be arranged into groups such that modules, cassettes consisting of multiple modules, or banks of cassettes can be backwashed simultaneously and/or sequentially.
  • a separate backwash/permeate system can be utilized for each group of modules (e.g., each cassette or banks of cassettes), while in certain embodiments of the systems illustrated in Figs. 3 to 5, the groups can be individually isolated for backwash or permeate flow via valves and valving functions.
  • a separate backwash and permeate system is not required for each group.
  • permeate and backwash pumps can be operated continuously while certain embodiments of the present systems step through the different groups.
  • the backwashing can be assisted via one or more of chemical addition, air addition, mechanical pulses, ultrasonic waves, and any other suitable methods that help remove fouling material.
  • the hollow fiber membrane modules can alternatively or additionally be rinsed or chemically cleaned periodically to remove fouling material that was not removed during backwashing.
  • Each of the systems of the present disclosure that are arranged into groups such as modules, cassettes and banks of cassettes can likewise be controlled via one or more controller as discussed above.
  • FIG. 6 another non-limiting embodiment of a membrane filtration system of the present disclosure is illustrated in which three separate treatment tanks 10a, 10b and 10c (referred to collectively as treatment tanks 10) are arranged so as to define multiple stages that are connected in series by conduits 17.
  • the multistage filtration system of Fig. 6 includes some of the same components described above in connection with Figs. 1 to 5. Those components in Fig. 6 are marked with the same or similar element numbers as used in Figs. 1 to 5. The description of those elements including each of the alternatives discussed above in connection with Figs. 1 to 5 apply in many respects to like element numbers in Fig. 6.
  • the one or more module 11 can be arranged into cassettes.
  • Each one or more module 11 can be contained in a respective one of the treatment tanks 10.
  • the one or more modules 11 can include headers attached to each hollow fiber membrane 12 to create a watertight connection between the outside of the membranes 12 and a permeate channel in the header.
  • the outer surface of the hollow fiber membranes 12 is in contact with the liquid feed and retentate.
  • a single treatment tank instead of having multiple separate treatment tanks defining each stage of the multistage system, includes, for example, dividers in the tank which separate and define each of the multiple stages of the multistage filtration system. [00125] To perform dead-end filtration in the multistage system of Fig.
  • the permeate is pumped or pulled through pores of the hollow fiber membranes in each stage of the system so that the permeate is withdrawn through the inside of the lumens of the hollow fiber membranes in each stage and a retentate is produced outside the lumens of the hollow fiber membranes in each stage.
  • a blower 13 can be utilized to push air through at least one conduit to distributer 14 to create air bubbles 15 that are released below the hollow fibers to create fluid movement and movement of the hollow fibers, which aids in reducing fouling and improving backwash efficiency.
  • the air bubbles can be released continuously, intermittently, or only during the backwash cycles.
  • the liquid feed enters treatment tank 10a (e.g., the first filtration stage) through at least one conduit and/or inlet via operation of valve 19 (e.g., receiving fluid from an algae source or container).
  • Permeate is withdrawn from treatment tank 10a through an outlet, through valve 21a and through a conduit into permeate siphon tank 41.
  • the retentate in treatment tank 10a travels through an outlet of tank 10a, through valve 18a, and through conduit 17a to an inlet of treatment tank 10b (e.g., the second filtration stage).
  • Permeate is withdrawn from treatment tank 10b through an outlet, through valve 21b, through a conduit and into permeate siphon tank 41.
  • the retentate in treatment tank 10b travels through an outlet in tank 10b, through valve 18b, through conduit 17b to treatment tank 10c (e.g., the third filtration stage).
  • Permeate is withdrawn from treatment tank 10c through an outlet of tank 10c, through valve 21c through a conduit into the permeate siphon tank 41.
  • the retentate in treatment tank 10c is withdrawn through a conduit via pump 16 (which conduit can include a valve operating with the conduit to allow or disallow the retentate to be withdrawn).
  • the liquid level in treatment tank 10a is controlled by intermittent opening of the feed valve 19.
  • the liquid level in treatment tanks 10b and 10c is maintained by gravity at the same level as treatment tank 10a, less the pressure drop to move through conduits 17a and 17b. It should be appreciated that the permeate withdrawn from each of treatment tank 10a, 10b, 10c can flow through a common conduit or permeate line to the permeate or permeate siphon tank 41.
  • valves 21a, 21b, 21c (referred to collectively as valves 21) and 23 are open, valves 25a, 25b, 25c (referred to collectively as valves 25) are closed, and permeate is pulled or withdrawn into the permeate siphon tank 41 through at least one conduit.
  • the suction or negative pressure is controlled by the height difference between the liquid in each of treatment tanks 10 and the permeate level in permeate siphon tank 41.
  • tank 10a can include a level sensor which can be used to sense or control the level of fluid for tank 10a.
  • Pump 42 is operated intermittently to maintain the level in siphon tank 41.
  • Valve 24 is opened and valve 23 is closed intermittently to maintain the fluid level in the elevated permeate gravity feed tank 40.
  • Each stage or tank in the system of Fig. 6 can be backwashed separately from each of the other stages or at the same time as any of the other stages.
  • a backwash sequence can be initiated for each stage in the same manner, namely by closing valve 21 for that respective stage, and opening valve 25 for that respective stage.
  • the backwash pressure is controlled by the difference in height of the permeate gravity feed tank 40 and the liquid level in whichever treatment tank 10a, 10b and/or 10c is being backwashed.
  • withdrawal of permeate is resumed by closing respective valve(s) 25 and opening respective valve(s) 21, depending upon which stages are being backwashed.
  • the backwash off-line period includes the time between stopping permeate flow from at least one of the modules 11 and restarting permeate flow from at least one of the modules 11.
  • the backwash off-line period includes one or more of: (i) the time to open and close valves 21 and 25 to stop permeate flow from module 11 and to start backwash flow to module 11; (ii) the time for the backwash flow; and (iii) the time to open and close valves 21 and 25 to stop backwash flow and resume permeate flow for filtration.
  • the backwash off-line period includes the time for each of
  • the backwash interval in an embodiment is the time between the start of one backwash cycle and the start of the next backwash cycle. It should be appreciated that the backwash off-line period and interval for the multistage systems and methods illustrated by Fig. 6 can be (a) an interval or period for one stage or tank of the plurality of tanks or stages in the system, or (b) an interval or period for multiple (including all or less than all) the stages or tanks of the plurality of stages or tanks.
  • the hollow fiber membrane area in each treatment tank or stage can be different (e.g., one or more earlier stages have a higher area while one or more later stages have a lower area), and (iii) the permeate withdrawal rate of each treatment tank or stage can be allowed to vary.
  • the suspended solids content of the retentate in Fig. 6 is higher inside treatment tank 10b then it is in treatment tank 10a, and higher in treatment tank 10c then it is in treatment tank 10b, and that the suspended solids content in each tank 10a, 10b, 10c will reach a natural equilibrium based upon the in-feed rate, the permeate withdrawal rate from each treatment tank, and the retentate discharge rate due to the operation of pump 16.
  • the multistage filtration system of Fig. 6 can operate at substantially the same maximum pressure drop or negative pressure at each stage (e.g., at each treatment tank 10a, 10b, 10c).
  • the negative pressure used to pull permeate through the pores of the hollow fiber membranes 12 positioned in tank 10a can be substantially the same negative pressure that is used to pull permeate through the pores of the hollow fiber membranes 12 positioned in each of tanks 10b and 10c.
  • the maximum pressure drop or negative pressure can be based upon physical limitations of the hollow fiber membranes, and that the flux can be lower in each successive stage in Fig.
  • each successive treatment tank 10a, 10b, and 10c due to the concentration of solid algae (due to the retentate produced) in each stage being higher while the pressure drop in each stage remains the same.
  • the backwash period and intervals for each stage or treatment tank can be adjusted independently to provide the highest net flux in each stage based upon, for example, the concentration level in that stage and/or the fouling characteristics of the algae.
  • the system is configured to automatically alter at least one of the backwash period or interval for one or more of the multiple stages based upon one or more solid algae concentration reading from at least one concentration sensor.
  • the one or more algae concentration sensors can be located, for example, in treatment tanks 10a, 10b or 10c, or in any other suitable location.
  • the system can be configured to determine the concentration attainment level based upon volumetric control, which can employ, for example a flow meter or any suitable flow and volumetric parameters.
  • the system is initially programmed or configured so that least one of the backwash period or interval of at least one of the stages is different from at least one of the other stages based upon known fouling characters of the algae in the algae slurry or in-feed.
  • the system of Fig. 6 when the system of Fig. 6 is first started or initiated, the system operates such that no retentate discharge occurs until a desired or predetermined suspended solids concentration level has been attained.
  • one or more algae concentration sensor can be utilized to determine when the predetermined or desired suspended concentration has been reached.
  • Such one or more sensor be located, for example, in treatment tanks 10a, 10b or 10c, or in any other suitable location.
  • the system can determine concentration by utilizing a flow meter and/or volumetric flow rate data, feed concentration data, and the tank volume.
  • the system is configured to gradually withdraw retentate or material (e.g., concentrated algae slurry) from treatment tank 10c via operation of pump 16 (e.g., a conduit and valve operating with pump 16 and coupled to tank 10).
  • retentate or material e.g., concentrated algae slurry
  • treatment tank 10c can be emptied, and optionally rinsed. To empty the tank, filtration is stopped by closing valves 25c, 21c, and 18b. The treatment tank 10c is then emptied via operation of pump 16 (e.g., a conduit and valve operating with pump 16 and coupled to tank 10). After tank 10c is emptied, a rinse can optionally be performed prior to restarting the filtration of tank 10c.
  • pump 16 e.g., a conduit and valve operating with pump 16 and coupled to tank 10.
  • treatment tank 10c is filled with water or cleaning solution, and cleaning valve 72c is opened so that water or solution can be added to tank 10c through valve 72c (e.g., the water or solution can come from a rinse source coupled fluidly with tank 10c via a conduit and valve 72c coupled to conduit 30c).
  • the rinse water or cleaning solution can be removed through an outlet or conduit via operation of pump 16 (e.g., opening a valve on a conduit or outlet and operating pump 16).
  • the water used for the rinse can also contain cleaning chemicals to aid in rinsing the tank or cleaning the membranes.
  • valve 18b can be opened to refill tank 10c, and the system can be operated using valves 25c and 21c for filtration and backwash with no retentate discharge until the desired solids concentration level is attained again.
  • This cycle of emptying the retentate and optionally rinsing the treatment tank 10c can be repeated one or more times.
  • one or more algae concentration sensor can again be utilized to determine when the desired concentration has been reached.
  • Such one or more sensor be located, for example, in treatment tanks 10a, 10b or 10c, or in any other suitable location.
  • the system can be configured to determine the concentration level attainment based upon volumetric control, which can utilize, for example, a flow meter or any known flow and/or volumetric parameters.
  • feed valve 18b can be closed and the liquid level in treatment tank 10c can be controlled by intermittent opening of feed valve 72c to add water or any other suitable replacement solution to replace the original media of the algae slurry (e.g., opening valve 72c coupled to a conduit or inlet, which conduit is also coupled to the water or solution source such as a container).
  • the water or replacement solution entering treatment tank 10c dilutes the original media and eventually replaces at least most of the media.
  • the media replacement level can be determined, monitored or sensed by any suitable sensor or sensing methods such as (i) sensing or determining the difference in conductivity, pH, ion specific electrode, or specific gravity of the algae slurry retentate or permeate relative to the initial value of the of the in the algae slurry retentate or permeate, or (ii) sensing or determining the level of media replacement through total volumetric throughput of rinse water or solution, measured, for example, by a rinse feed flow meter or permeate flow meter, relative to the total volume of treatment tank 10c.
  • any suitable sensor or sensing methods such as (i) sensing or determining the difference in conductivity, pH, ion specific electrode, or specific gravity of the algae slurry retentate or permeate relative to the initial value of the of the in the algae slurry retentate or permeate, or (ii) sensing or determining the level of media replacement through total volumetric throughput of rinse water or solution, measured, for example, by a rinse
  • the rinsed algae slurry retentate can be removed from treatment tank 10c through an outlet or conduit via operation of pump 16 (e.g., opening a valve coupled to the outlet or conduit and operating pump 16).
  • the system of Fig. 6 can include one or more controller, which can be programmed or configured to operate with one or more of the valves, the blower, one or more of the pumps, any sensors, any flow meters, and/or any other system components so as to perform various functions of the system including valving, pumping, backwashing, rinsing, filtration, permeate flow, or any other system functions.
  • the one or more controller can include at least one processor and at least one memory device which stores instructions, which when executed by the at least one processor, cause the at least one processor to operate with one or more of the valves, the pumps, any sensors and any other components to perform operations of the filtration system.
  • Various embodiments of the Fig. 6 system can also include at least one input device and/or at least one display device, and the one or more controller can be programmed or configured to operate with the at least at least one input device and/or at least one display device.
  • Fig. 7 illustrates another embodiment of a multistage hollow fiber dead-end filtration system of the present disclosure in which the system includes a transfer tank that enables cleaning or isolation of one of the multiple stages or tanks while maintaining filtration or flow through the other stages or tanks. That is, the system of Fig. 7 illustrates a multistage hollow fiber dead-end filtration system for isolating individual treatment tanks or stages so that the isolated stage or tank, including its hollow fiber membranes, can be cleaned or rinsed while the other treatment tanks or stages remain on-line or in filtration mode.
  • the system of Fig. 7 operates in substantially the same manner as described above for Fig. 6 during filtration and backwashing with valves 31, 32, 36a, 36b, and 36c closed; pumps 33 and 34 off; and three-way valve 37 closed to treatment tank 10b.
  • the system of Fig. 7 also includes many of the same components described above in connection with Figs. 1 to 6. Those components in Fig. 6 are marked with the same or similar element numbers as used in Figs. 1 to 6. The description of those elements including each of the alternatives discussed above in connection with Figs. 1 to 6 apply in many respects to like element numbers in Fig. 7.
  • a liquid level sensor can also be included in each of tanks 10b and 10c (for the system of Figs 6 and 7).
  • the system can utilize each sensor when a respective treatment tank 10a, 10b, or 10c receives in-feed so as to sense and control the level of liquid in the respective tank.
  • the system of Fig. 7 operates according to the following sequence: close valves 18a and 21a, turn three-way valve 37 from treatment tank 10a to treatment tank 10b; open valve 31 and utilize pump 33 to transfer retentate from treatment tank 10a to a transfer tank 35 through at least one conduit; close valve 31 and add water with or without cleaning chemicals to treatment tank 10a through at least one inlet or conduit via operation of valve 72a (e.g., opening valve 72a and allowing fluid to flow from a source or container through a conduit to tank 10a); soak the membrane in treatment tank 10a for a desired or predetermined cleaning time with continuous, intermittent, or no air bubbling through diffuser 12a; drain treatment tank 10a through an outlet or conduit via operation of valve 36a; close valve 36a, turn three- way valve 37 from treatment tank 10b to treatment tank 10a to fill treatment tank 10a
  • close valves 18a and 21a turn three-way valve 37 from treatment tank 10a to treatment tank 10b
  • transfer tank 35 is processed to control the level in treatment tank 10b by allowing fluid to flow from treatment tank 10b through a conduit or outlet via operation of pump 34, and control the level in treatment tank 10c through operation of valve 38.
  • transfer tank 35 is emptied, the level in treatment tank 10b is controlled through intermittent operation of valve 19, and three-way valve 37 is opened for normal operation of treatment tank 10b.
  • valves 18a and 21b To clean treatment tank 10b while treatment tanks 10a and 10c remain in dead-end filtration or on-line, the system of Fig. 7 performs the following sequence: close valves 18a and 21b; close valve 37, open valve 32 and utilize pump 33 to transfer the retentate from treatment tank 10b to transfer tank 35 through at least one conduit; close valve 18b and add water with cleaning chemicals through to treatment tank 10b through operation of valve 72b (e.g., opening valve 72b and allowing fluid to flow from a source or container through a conduit to tank 10b); soak the membrane in treatment tank 10b for a predetermined or desired cleaning time with continuous, intermittent, or no air bubbling through diffuser 12b; drain treatment tank 10b through valve 36b; close valve 36b; open valve 18a and 21b, and close valves 31 and 32 to resume normal operation.
  • valve 72b e.g., opening valve 72b and allowing fluid to flow from a source or container through a conduit to tank 10b
  • treatment tank 35 is processed by controlling the level in treatment tank 10c through operation of pump 34 with valve 38 open and valve 32 closed. Once transfer tank 35 is emptied, valves 31, 32 and 37 are opened for normal operation of treatment tank 10c.
  • the multistage filtration system of Fig. 7 can operate at substantially the same maximum pressure drop or negative pressure at each stage (e.g., at each treatment tank 10a, 10b, IOC).
  • the negative pressure used to pull permeate through the pores of the hollow fiber membranes 12 positioned in tank 10a can be substantially the same negative pressure used to pull permeate through the pores of the hollow fiber membranes 12 positioned in each of tanks 10b and 10c.
  • the maximum pressure drop or negative pressure can be based upon physical limitations of the hollow fiber membranes, and that the flux is lower in each successive stage in Fig.
  • each successive treatment tank 10a, 10b, 10c due to the concentration of solid algae (due to the retentate produced) in each stage being higher while the pressure drop in each stage remains substantially the same.
  • the backwash period and intervals for each stage or treatment tank can be adjusted independently to provide the highest net flux in each stage based upon, for example, the concentration level in that stage and/or the fouling characteristics of the algae.
  • the system is configured to automatically alter at least one of the backwash period or interval for one or more of the multiple stages based upon one or more solid algae concentration reading from at least one concentration sensor.
  • the system is initially programmed or configured so that least one of the backwash period or interval of at least one of the stages is different from at least one of the other stages based upon known fouling characters of the algae in the algae slurry.
  • the system of Fig. 7 when the system of Fig. 7 is first started or initiated, the system operates in manner such that no retentate discharge occurs until a desired or predetermined suspended solids concentration level has been attained.
  • one or more concentration sensor can again be utilized to determine when the desired concentration has been reached.
  • Such one or more sensor be located, for example, in treatment tanks 10a, 10b or 10c, or in any other suitable location.
  • the system of Fig. 7 can be configured to determine the concentration level attainment based upon volumetric control, which can utilize, for example, a flow meter or any known flow and/or volumetric parameters.
  • the system is configured to gradually withdraw retentate or material (e.g., concentrated algae slurry) from treatment tank 10c via operation of pump 16 so as to maintain the predetermined level of concentration (e.g., opening a valve on a conduit with which pump 16 operates).
  • retentate or material e.g., concentrated algae slurry
  • treatment tank 10c can be emptied and optionally rinsed. To empty the tank, filtration is stopped by closing valves 25c, 21c and 18b. Treatment tank 10c can then emptied via operation of pump 16 (e.g., opening a valve on a conduit with which pump 16 operates). After tank 10c is emptied, a rinse can optionally preformed prior to restarting the filtration of tank 10c.
  • pump 16 e.g., opening a valve on a conduit with which pump 16 operates.
  • treatment tank 10c is filled with water or cleaning solution by opening cleaning valve 72c so that the water or solution can be added to tank 10c through valve 10c (e.g., allowing fluid to flow from a source or container through at least one conduit or inlet via opening valve 10c).
  • valve 10c e.g., allowing fluid to flow from a source or container through at least one conduit or inlet via opening valve 10c.
  • the rinse water or cleaning solution can be removed via pump 16.
  • the water used for the rinse can also contain cleaning chemicals to aid in rinsing the tank or cleaning the membranes.
  • valve 18b can be opened to refill tank 10c, and then the system can be operated using valves 25c and 21c for filtration and backwash with no retentate discharge until the desired solids concentration level is attained again.
  • one or more concentration sensor can again be utilized to determine when the desired concentration has been reached. Such one or more sensor be located, for example, in treatment tanks 10a, 10b or 10c, or in any other suitable location.
  • the system can be configured to determine the concentration level attainment based upon volumetric control, which can utilize, for example, a flow meter or any known flow and/or volumetric parameters.
  • volumetric control which can utilize, for example, a flow meter or any known flow and/or volumetric parameters.
  • feed valve 18b can be closed and the liquid level in treatment tank 10c can be controlled by intermittent opening of the feed valve 72c to add water or any other suitable replacement solution to replace the original media of the algae slurry.
  • the water or replacement solution entering treatment tank 10c dilutes the original media and eventually replaces at least most of the media.
  • the media replacement level can be monitored, sensed or determined by any suitable sensor or sensing methods such as (i) sensing or determining the difference in conductivity, pH, ion specific electrode, or specific gravity of the algae slurry retentate or permeate relative to the initial value of the of the in the algae slurry retentate or permeate, or (ii) sensing or determining the level of media replacement through total volumetric throughput of rinse water or solution, measured, for example, by a rinse feed flow meter or permeate flow meter, relative to the total volume of treatment tank 10c.
  • any suitable sensor or sensing methods such as (i) sensing or determining the difference in conductivity, pH, ion specific electrode, or specific gravity of the algae slurry retentate or permeate relative to the initial value of the of the in the algae slurry retentate or permeate, or (ii) sensing or determining the level of media replacement through total volumetric throughput of rinse water or solution, measured, for example, by a rinse
  • Examples of media sensor include (i) a conductivity meter in the algae slurry in the at least one treatment tank or in the permeate leaving the at least one permeate conduit, (ii) a pH meter for the algae slurry in the at least one treatment tank or in the permeate leaving the through the at least one permeate conduit, (iii) a flow meter for the rinse fluid entering the at least one treatment tank, or (iv) a flow meter for the permeate leaving the at least one treatment tank.
  • the system of Fig. 7 can also include one or more controller, which can be programmed or configured to operate with one or more of the valves, the blower, one or more of the pumps, any sensors and/or any other system components so as to perform various functions of the system including valving, pumping, backwashing, rinsing, filtration, permeate flow or any other system functions.
  • the one or more controller can include at least one processor and at least one memory device which stores instructions, which when executed by the at least one processor, cause the at least one processor to operate with one or more of the valves, the pumps, any sensors and any other components to perform operations of the filtration system.
  • Various embodiments of the system of Fig. 7 can also include at least one input device and/or at least one display device, and the one or more controller can be programmed or configured to operate with the at least at least one input device and/or at least one display device.
  • the suspended solids content of the retentate in Fig. 7 is higher inside treatment tank 10b then it is in treatment tank 10a, and higher in treatment tank 10c then it is in treatment tank 10b, and that the suspended solids content in each tank 10a, 10b, 10c will reach a natural equilibrium based upon the in-feed rate, the permeate withdrawal rate from each treatment tank, and the retentate discharge rate due to the operation of pump 16.
  • Figs. 6 and 7 in the form of three differed treatment tanks
  • additional or fewer stages can be utilized (e.g., additional or fewer tanks).
  • more than three stages can be utilized by adding additional treatment tanks with associated piping and valves.
  • two stages can be used by eliminating treatment tank 10b, along with its associated piping and valves.
  • the system can include a single treatment tank having multiple stages defined by one or more divider separating the single treatment tank into different spaces or stages, rather than multiple separate tanks.
  • the systems of Figs. 6 and 7 can be arranged into groups such that modules, cassettes of modules, or banks of cassettes can be operated together as a single unit, and one or more stages can include two or more treatment tanks operated in parallel.
  • a media rinse can also be incorporated into stages other than the final stage by adding isolation or bypass valves and a water inlet valve.
  • Backwash can be assisted in various embodiments with the addition of chemicals, air, mechanical pulses, ultrasonic waves, and any other suitable methods.
  • Modules or cassettes can also be rinsed or chemically cleaned periodically so that any fouling material that is not removed by backwashing is removed.
  • FIGs. 8 and 9 illustrate embodiments of treatment tanks 10 for use with any of the hollow fiber membrane filtration systems of the present disclosure (e.g., the multi-stage hollow fiber membrane filtration systems of Figs. 6 and 7).
  • Tanks 10 each include a plurality of modules 11 contained within the tanks 10.
  • Each module 11 has a plurality of hollow fiber membranes.
  • Each of the modules 11 can be arranged or grouped into cassettes (as discussed above), and the cassettes can be grouped into banks as discussed above.
  • Each tank 10 can include a single module or multiple modules arranged into multiple cassettes.
  • Tank 10 of Fig. 8 can include one or more of plastic, metal, concrete and has generally vertical side walls extending from a generally horizontal base wall.
  • Tank 10 of Fig. 9 is an earthen lined tank or pond having generally angled side walls extending from a generally horizontal base wall, each wall formed by the earth.
  • each of the side walls of earthen tank 10 extends at an angle from a vertical axis (e.g., 45 degrees from a vertical axis), and can include a lining to aid in containing or holding the in-feed algae or biological slurry inside the treatment tank 10.
  • the lining of the earthen tank or pond 10 in Fig. 9 in one example includes plastic such as high-density polyethylene.
  • the angled side walls formed by the earth allow a greater volume of liquid in-feed (e.g., and algae or biological slurry) to be contained within the earthen treatment tank 10, which can be detrimental in a single stage system, but can be suitable in multistage systems, as discussed below.
  • the lined earthen treatment tank 10 is advantageous in that it is generally less expensive than concrete, plastic and/or metal treatment tanks. It should be appreciated that the packing density of the hollow fiber membranes in Fig. 8 (i.e., the area of the hollow fiber membranes relative to the total volume of tank 10 or the volume of fluid that is contained within tank 10) is greater than the packing density of the hollow fiber membranes in Fig. 9. In other words, the concrete, metal or plastic tank 10 of Fig.
  • FIG. 8 one non-limiting embodiment of an algae harvesting and cultivation system of the present disclosure is illustrated in which carbon dioxide can be added, permeate can be re-used for cultivation, and live algae retentate can be attained.
  • the system of Fig. 10 includes an algae cultivator 60 having one or more algae cultivation device 60a, 60b, 60c, such as one or more open raceway, closed photobioreactor, heterotrophic reactor, or a combination of open raceway closed photobioreactors, or heterotrophic reactors, or any other suitable algae cultivation devices.
  • Nutrients, make-up water, carbon dioxide, and other material for cultivation of the algae can be added to algae cultivator 60 as needed to attain desired growth conditions.
  • the media containing algae can flow or otherwise be transferred from cultivator 60 (e.g., allowing the fluid to flow from the cultivator through one or more conduit via gravity, or in some embodiments pumping the fluid to the cultivator through the at least one conduit using pump 61) into a hollow fiber dead-end filtration system 50, such as one or more of the dead-end filtration systems described herein.
  • the dead-end filtration system includes a plurality of filtration stages (e.g., the systems of Figs. 6 and 7).
  • a recycled media hold-up reservoir 63 in fluid communication with the dead-end filtration system can receive and store recycled media from the dead-end filtration system 50a, at least until the media is needed again in the algae cultivator 60. If a portion or all of the media needs to be replaced, then the media can be discharged through a drain outlet or conduit 52 (e.g., via operating a valve on the conduit), and the new media can be added to the cultivator 60. Nutrients such as carbon dioxide can be mixed with the recycled media in a nutrient supply contactor 66 that can be in fluid communication with the hold-up reservoir 63 or the dead-end filtration system 50 (e.g., through one or more conduit for each).
  • Non-limiting examples of nutrient supply contactor 66 include a mixing nozzle in the recycled media conduit, a two-phase static mixer or a packed bed absorber.
  • the permeate can then flow or otherwise be transferred or recycled back to the cultivation system 60 (e.g., flowing the permeate through at least one conduit, which in some embodiments can be achieved via gravity or via pump 62).
  • the retentate can be rinsed, for example, according to any of the rinsing procedures or sequences described herein.
  • rinsing can be performed by stopping the liquid in-feed to filtration system 50 (or stopping the feed to a last stage of filtration system 50 in a multistage filtration system such as the systems illustrated by Fig. 6 or 7), and feeding water to the filtration system 50 (or feeding water to the last stage of filtration system 50 in a multistage filtration system such as the systems of Figs. 6 or 7) to displace the media.
  • the permeate recovered during the rinsing can added to the recycled media or discharged from the system.
  • the rinsed, concentrated algae slurry obtained from the hollow fiber dead-end filtration system 50 can then be discharged for further treatment, re-cultivation, or storage. If pre-treatment is used, the type of pre-treatment can depend upon the algae and the algae product.
  • the concentrated algae slurry retentate from the hollow fiber dead-end filtration system 50 can be removed via an outlet or conduit 51 where the algae slurry can be held or stored in, for example, an algae container.
  • the algae in the retentate is typically viable and can be re-cultivated or stored and then re-cultivated.
  • cultivator 60 needs to be temporarily stopped, for example, to avoid dilution in a large rain event or to avoid overheating in high temperature event, or if the media needs to be replaced, for example because of dissolved organics or inorganics, then the all of the algae can be harvested by transferring all of the media containing the algae via pump 61 from algae cultivator 60 to the dead-end filtration system 50.
  • the permeate can be discharged through drain outlet or conduit 52, or stored in the recycled permeate hold-up reservoir 63 (e.g., via the permeate flowing or otherwise being transferred to the at least one cultivator through for example at least one conduit).
  • the retentate can optionally be rinsed as described herein, and then re-cultivated in algae cultivator 60 with new media. If the algae is to be stored before re cultivation then the algae slurry retentate removed via outlet or conduit 51 can be packaged and stored at a cold temperature, e.g. less than 4°C, until the retentate will be used for re cultivation.
  • a cold temperature e.g. less than 4°C
  • the algae needs to be stored for re-cultivation at a later time, for example, to supply the algae to a separate cultivation facility, to use the algae as live feed at a separate aquaculture facility, or to provide storage of algae for inoculation if the algae cultivator 60 needs to be restarted, all or a portion of the algae can be harvested by transferring or allowing all of the media containing the algae to flow or otherwise be transferred (e.g., via pumping the algae from cultivator 60 through at least one conduit via pump 61) to the dead-end filtration system 50.
  • the permeate can be stored in a recycled permeate hold-up reservoir 63, which can be in fluid communication with the hollow fiber filtration system 50 via at least one conduit, and recycled.
  • the retentate can optionally be rinsed according to any rinse procedure described herein, and re-cultivated in cultivator 60 with new media. If the algae is to be stored before re-cultivation, then the algae slurry retentate can be removed via an outlet or conduit 51 to, for example, at least one algae container, and can be packaged and stored at cold temperatures, e.g. less than 4°C, until re-cultivation.
  • the media for algae cultivator 60 contains sodium bicarbonate and sodium carbonate. As the algae undergoes photosynthesis, carbon dioxide is consumed to make biomass. As carbon dioxide is consumed, sodium bicarbonate is converted to sodium carbonate. When a portion or all of the algae is ready to be harvested, the media containing algae flows or is transferred (e.g., pumping the algae through at least one conduit via pump 61) from algae cultivator 60 to hollow fiber dead-end filtration system 50, such as one or more of the dead-end filtration systems described herein including any of the systems having multiple stages or treatment tanks.
  • a permeate is obtained from the hollow fiber dead-end filtration system 50 and can be transferred or stored in a recycled media hold-up reservoir 63 (e.g., via the permeate flowing or otherwise being transferred or pumped through at least one conduit to the reservoir 63) until the recycled media is needed for cultivation.
  • Carbon dioxide can be mixed with the recycled media in a nutrient or carbon dioxide adder or supply contactor 66 that is in fluid communication with the reservoir 63 (e.g., via one or more fluid conduit).
  • a contactor include a mixing nozzle in the recycled media conduit, a two-phase static mixer or a packed bed absorber. When the carbon dioxide dissolves in the media, sodium carbonate is converted back to sodium bicarbonate.
  • the carbonated recycled media can flow or otherwise be transferred back to the algae cultivator 60 (e.g., by pumping the media through at least one conduit via pump 62 or via gravity flowing the media) and the above cycle can be repeated. It should be recognized that the carbon dioxide can be added before or after pump 62, and that a carbonated media hold-up reservoir 63 could be added to store the carbonated media prior to transferring the media to the cultivator 60.
  • FIG. 12 one non-limiting embodiment of a harvesting and cultivation system is illustrated in which the media is recharged with carbon dioxide through an absorber 66 prior to recycling the media to algae cultivator 60.
  • Absorber 66 of Fig. 12 and any other absorbers of the present disclosure can operate via a blower or via a pressure difference between an inlet and outlet of absorber 66.
  • the system of Fig. 12 includes many of the same components described above in connection with Figs. 10 and 11. Those components in Fig. 12 are marked with the same or similar element numbers as used in Figs. 10 and 11. The description of those elements including each of the alternatives discussed above in connection with Figs. 10 and 11 apply in many respect to like element numbers in Fig 12.
  • the system of Fig. 12 operates such that when a portion or all of the algae is ready to be harvested after cultivating in algae cultivator 60, the media containing algae and sodium carbonate can flow or otherwise be transferred from algae cultivator 60 to hollow fiber dead end filtration system 50 (e.g., flowing the algae through at least one conduit, which in an embodiment can be achieved via gravity or pump 61).
  • the dead-end filtration system can be one or more of the dead-end filtration systems described herein including the multistage systems such as Figs. 6 and 7.
  • the permeate obtained from hollow fiber dead-end filtration system 50 e.g., any of the dead-end filtration systems described herein including the multistage systems such as Figs.
  • the recycled media can flow or otherwise be transferred (e.g., via the permeate flowing through at least one conduit which in an embodiment can be achieved via gravity) and stored in a recycled media hold-up reservoir 63 until the media is needed in the packed bed absorber 66.
  • the recycled media can flow or otherwise be transferred from reservoir 63 to packed bed absorber 66 (e.g., the media flowing through at least one conduit, which in an embodiment can be achieved via gravity or via pump 65).
  • the recycled media can flow through the packed bed absorber 66 (e.g., via gravity).
  • the recycled media contacts a gas containing carbon dioxide in the packed bed absorber 66, where the sodium carbonate in the media is converted to sodium bicarbonate resulting in a carbonated media.
  • the carbon dioxide containing gas can enter the absorber 66 through a gas inlet or conduit 68, which in an embodiment can be located at the bottom of packed bed absorber 66.
  • the carbon dioxide absorbed by the recycled media in the packed bed absorber 66 reduces the concentration of carbon dioxide in the gas.
  • the carbon dioxide depleted gas can exit the absorber 66 through a gas outlet or conduit 69, which in an embodiment can be located at the top of the absorber 66.
  • the carbonated media can flow or otherwise be transferred from the absorber to a storage carbonate media hold-up reservoir 67 (e.g., via the fluid flowing through at least one conduit, which in an embodiment can be achieved via gravity).
  • the reservoir 67 can be covered with a carbon dioxide retaining lid or cover so that the carbon dioxide does not escape into the atmosphere.
  • the carbonated media can flow or otherwise be transferred from the carbonated media hold-up reservoir 67 back to the algae cultivator 60 (e.g., via flowing the carbonated media through at least one conduit, which in one embodiment can be achieved via gravity or via pump 62).
  • any conduit between the hold-up reservoir 67 and algae cultivator 60 can be enclosed so that the carbon dioxide does not escape to the atmosphere. Examples of enclosed conduits include a pipe or a covered, lined aqueduct.
  • the absorber 66 can include multiple packed bed columns instead of a single packed bed column. If multiple packed bed columns are used, the gas and liquid fluid can flow through the columns in series or in parallel.
  • FIG. 13 one non-limiting embodiment of a harvesting and cultivation system of the present disclosure is illustrated in which separate media is used in each cultivation stage.
  • the system of Fig. 13 cultivates algae in a first algae cultivator 60 which defines a first cultivation stage, and a separate second algae cultivator 80 which defines a second cultivation stage.
  • the cultivation and harvesting system of Fig. 13 includes many of the same components described above in connection with Fig. 10-12. Those components in Fig. IB are marked with the same or similar element numbers as used in Figs. 10-12.
  • First cultivation stage 60 can include one or more algae cultivation device 60a, 60b, 60c, such as one or more open raceway, closed photobioreactor, heterotrophic reactor, or a combination of open raceway closed photobioreactors, or heterotrophic reactors, or any other suitable algae cultivation devices. Nutrients, make-up water, carbon dioxide, and other material for cultivation of the algae can be added to first cultivation stage 60 as needed to attain desired growth conditions.
  • the first stage media containing algae can flow or otherwise be transferred from first cultivation stage 60 to a first hollow fiber dead-end filtration system 50a, such as one or more of the dead-end filtration systems described herein including the multi-stage systems of Figs. 6 and 7.
  • the first stage media containing algae can flow or otherwise be transferred through at least one conduit, which in an embodiment can be achieved via gravity flow through at least one conduit or via pumping the media through the at least one conduit via pump 61.
  • the permeate obtained from the first hollow fiber dead-end filtration system 50a can flow or otherwise be transferred and recycled back to the first cultivation stage 60 (e.g., flowing the permeate through at least one conduit to the first cultivation stage 60, which in an embodiment can be achieved via gravity or pump 62).
  • a recycled media hold-up reservoir 63 for the first stage recycled media can be in fluid communication with the first filtration system 50a (e.g., at least one conduit via gravity) and be used to store the recycled media until the media is needed in the first cultivation stage 60.
  • the permeate from the first filtration system 50a can flow or otherwise be transferred from filtration system 50a to the reservoir 63 through at least one conduit which can be achieved via gravity in an embodiment, and then recycled media held in the reservoir 63 can be transferred or otherwise flow from the reservoir back to the first cultivation stage 60 through at least one other conduit, which in an embodiment can be achieved via gravity or pump 62. If the elevation of the permeate outlet of filtration system 50a is higher than the elevation of reservoir 63, then the recycled media can flow from filtration system 50a to the reservoir 63 by gravity. If the elevation of the reservoir 63 is higher than the elevation of the inlet section of the first cultivation stage 60, then the recycled media can also flow from reservoir 63 to first cultivation stage 60 by gravity.
  • the first stage media can be rinsed according to any rinse method or sequence described herein. Rinsing can be performed by stopping the liquid in-feed to the filtration system (or stopping the last stage of filtration in a multi-stage filtration system), and feeding water or other suitable rinsing solution to the system to displace the first cultivation stage media (e.g. feeding water or solution from a source or container). The permeate recovered during the rinsing can be added to the first stage recycled media or discharged from the system.
  • the rinsed, concentrated algae slurry obtained from the hollow fiber dead-end filtration system 50a can flow or otherwise be transferred (e.g., flow through at least one conduit which in an embodiment can be achieved via gravity) to a pre-treatment system 70 to be pretreated as described herein.
  • the type of pre-treatment can depend upon the algae and the algae product. For example, chemical treatment, ozone, low concentration of bleach, an acid or a base can be used to stress the algae to induce oil formation in the second algae cultivation stage.
  • the algae is mixed with a chemical in a tank for a short period of time (e.g., less than 1 hour) prior to algae flowing or otherwise being transferred to the second cultivation stage 80 and dilution in the second stage media.
  • the rinsed, concentrated algae slurry can then flow or otherwise be transferred to second cultivation stage 80 (e.g., flowing the rinsed concentrated algae slurry through at least one conduit, which in an embodiment can be achieved via gravity or pump 71), where additional algae can be cultivated in a second cultivation stage media, which can be different from the first cultivation stage media.
  • the second cultivation stage 80 also includes one or more algae cultivation devices 80a, 80b, 80c, such as an open raceway, a closed photobioreactor, a combination of open raceways and closed photobioreactors, a heterotrophic reactor, or any other suitable algae cultivation devices.
  • the algae slurry can flow from cultivation stage 60 to filtration system 50a by gravity. If the outlet of the recycled media from filtration system 50a is higher in elevation than the inlet of cultivation stage 60, then the recycled media can flow back to cultivation stage 60 from the filtration system 50a by gravity. If the retentate outlet of filtration system 50a is higher in elevation than the inlet section of cultivation stage 80, then the retentate algae slurry can flow by gravity from filtration system 50a to cultivation stage 80.
  • the second stage media containing the additional algae can flow or otherwise be transferred (e.g., flowing the additional algae through at least one conduit, which in an embodiment can be achieved via gravity or pump 81) from the second cultivation stage 80 to a hollow fiber dead-end filtration system 50b, such as one or more of the hollow fiber dead-end filtration systems described herein including the multistage systems.
  • the permeate obtained from hollow fiber dead-end filtration system 50b can flow or otherwise be transferred or recycled back to second cultivation stage 80 (e.g., flowing the permeate through at least one conduit, which in an embodiment can be achieved via gravity or pump 82).
  • a recycled media hold-up reservoir 83 can be in fluid communication with the hollow fiber dead-end filtration system 50b and can be used to store the recycled media until the recycled media is needed in the second cultivation stage 80.
  • the permeate from second filtration system 50b can flow or otherwise be transferred from system 50b to reservoir 83 through at least one conduit, and the recycled media held in the reservoir 83 can be transferred or otherwise flow from reservoir 83 back to second cultivation stage 80 through at least one other conduit, which in an embodiment can be achieved via gravity or pump 82.
  • the concentrated algae slurry product obtained from the dead end filtration system 50b can be rinsed according to any rinsing method or sequence described herein prior to removal of the concentrated algae through an outlet or conduit 84.
  • the permeate obtained during the rinsing can either be added to the second stage recycled media or discharged from the system.
  • Fig. 14 a non-limiting embodiment of a process or method for cultivating and harvesting algae in an algae harvesting and cultivation system of the present disclosure is illustrated in which separate media is used for each stage of cultivation.
  • media, nutrients, and/or carbon dioxide can be added to support algae growth of, for example, an algae inoculum.
  • the media can contain water with any desired dissolved solids. Evaporation of liquid can take place during the first cultivation stage, so make-up water can be added to maintain the media composition.
  • the algae cultivated in the first stage can be harvested through a first hollow fiber dead-end filtration system, such as one or more of the systems described herein in which there is low shear stress so that the algae remains intact, and viable algae cells can be recovered in the retentate.
  • Permeate from the first dead-end filtration system can be recycled back to the first cultivation stage of the system.
  • At least a portion of the make-up water needed to maintain the media concentration in the cultivation stage can be used to rinse the algae, and the rinse permeate can also be recycled back to the first cultivation stage so that substantially all of the dissolved components are recovered in the recycled permeate and rinse water.
  • the retentate produced from the first dead-end filtration system can therefore be free or substantially free of any components from the first cultivation stage.
  • the algae produced from the first cultivation stage and the first hollow fiber dead end filtration system can then be pretreated to impart stress, and a chemical trigger can be added for secondary metabolite formation. Other adjustments can also be made to induce algae product formation in the second algae cultivation.
  • media, nutrients, and carbon dioxide can again be added to support additional algae product formation. Evaporation of liquids can also take place during the second cultivation stage.
  • the algae from the second cultivation stage can be harvested through a second hollow fiber dead end filtration system, such as one or more of the systems described herein with low shear stress on the algae.
  • the permeate from the second dead-end filtration system can be recycled to the second cultivation stage.
  • Water can again evaporate from the system, so make-up or additional water can be added to maintain the media composition. At least a portion of the make-up water can be used to rinse the additional algae, and the rinse permeate can be recycled back to the second cultivation stage so that all or substantially all of the dissolved components are recovered in the recycled permeate and rinse water. Any needed processing additives such as acids, bases, salts or polymers can be added to the concentrated slurry, and the algae slurry can be processed to recover algae products.
  • the systems and methods discussed above with respect to Figs. IB and 14 enable algae to be cultivated and harvested using two separate media that can have different osmotic strength, pH, nutrient loading, and/or chemical triggers without contaminating one media with the other media or needing the first stage media to be treated prior to entering the second stage of cultivation.
  • the systems and methods also enable a rapid change from the first media to the second media without requiring large chemical additions to change the first stage media composition to the second stage media composition.
  • the systems and methods allow adjustments to be made for processing the algae slurry into a product, such as a pH change, without requiring large chemical additions to change the second stage media composition.
  • the process and systems also enable recovery of substantially all of the dissolved solids in each media, and substantially eliminates the dissolved solids content in the harvested algae slurry.
  • FIG. 15 one non-limiting embodiment of an algae harvesting and cultivation system of the present disclosure is illustrated in which carbon dioxide can be added and separate media can be used in each cultivation stage.
  • the system of Fig. 15 cultivates algae in a first algae cultivator 60 defining a first cultivation stage, and a separate second algae cultivator 80 defining a second cultivation stage.
  • the system of Fig. 15 also includes a first dead-end hollow fiber filtration system 50a, a carbon dioxide absorber 66, and a second dead end hollow fiber filtration system 50b and another carbon dioxide absorber 86.
  • Fig. 15 includes many of the same components described above in connection with Figs. 12 and 13. Those components in Fig. 15 are marked with the same or similar element numbers as used in Figs. 12 and 13. The description of those elements including each of the alternatives discussed above in connection with Figs. 12 and 13 apply in many respect to like element numbers in Fig 15.
  • the system of Fig. 15 operates in an embodiment such that when a portion or all of the algae is ready to be harvested after cultivating in algae cultivator 60, the media containing algae and sodium carbonate can flow or otherwise be transferred from algae cultivator 60 to hollow fiber dead-end filtration system 50a (e.g., flowing the algae from cultivator 60 to dead- end filtration system 50a through at least one conduit, which in an embodiment can be achieved via gravity or pump 61).
  • the dead-end filtration system 50a can be one or more of the dead-end filtration systems described herein including the multi-stage systems such as Figs. 6 and 7.
  • the permeate obtained from hollow fiber dead-end filtration system 50a can flow or otherwise be transferred (e.g., the permeate flowing through at least one conduit which in an embodiment can be achieved via gravity) and stored in a recycled media hold-up reservoir 63 until the media is needed in a packed bed absorber 66.
  • the recycled media in reservoir 63 can flow or otherwise be transferred from reservoir 63 to packed bed absorber 66 (e.g., flowing the recycled media through at least one conduit, which in an embodiment can be achieved via gravity or pump 65).
  • the recycled media can flow through packed bed absorber 66 (e.g., via gravity) where the media contacts a gas containing carbon dioxide in the absorber 66 and sodium carbonate in the media can be converted to sodium bicarbonate resulting in a carbonated media.
  • the carbon dioxide containing gas can enter the absorber 66 through a gas inlet or conduit 68, which in an embodiment can be located at the bottom of packed bed absorber 66.
  • the carbon dioxide absorbed by the recycled media in the packed bed absorber 66 reduces the concentration of carbon dioxide in the gas.
  • the carbon dioxide depleted gas can exit the absorber 66 through a gas outlet or conduit 69, which in an embodiment can be located at the top of absorber 66.
  • the carbonated media can flow or otherwise be transferred from absorber 66 to a storage carbonate media hold-up reservoir 67 (e.g., via the fluid flowing through at least one conduit, which can be achieved in an embodiment via gravity).
  • the reservoir 67 can be covered with a carbon dioxide retaining lid or cover so that the carbon dioxide does not escape into the atmosphere.
  • the carbonated media can flow or otherwise be transferred from the carbonated media hold-up reservoir 67 back to the algae cultivator 60 (e.g., flowing the carbonated media through at least one conduit, which in an embodiment can be achieved via gravity or pump 62).
  • any conduit between the hold-up reservoir 67 and first algae cultivator or stage 60 can be enclosed so that the carbon dioxide does not escape to the atmosphere. Examples of enclosed conduits include a pipe or a covered, lined aqueduct.
  • absorber 66 can include multiple packed bed columns instead of a single packed bed column. If multiple packed bed columns are used, the gas and liquid fluid can flow through the columns in series or in parallel.
  • First algae cultivator or stage 60 can include one or more algae cultivation device 60a, 60b, 60c, such as one or more open raceway, closed photobioreactor, heterotrophic reactor, or a combination of open raceway closed photobioreactors, or heterotrophic reactors, or any other suitable algae cultivation devices.
  • Nutrients, make-up water, carbon dioxide, and other material for cultivation of the algae can be added to first cultivation stage 60 as needed to attain desired growth conditions.
  • the first stage media can be rinsed according to any rinse method or sequence described herein. Rinsing can be performed by stopping the liquid in-feed to the filtration system (or stopping the last stage of filtration in a multi-stage filtration system), and feeding water or other suitable rinsing solution to the system to displace the first cultivation stage media. The permeate recovered during the rinsing can be added to the first stage recycled media or discharged from the system.
  • the rinsed, concentrated algae slurry obtained from the hollow fiber dead-end filtration system 50a can flow or otherwise be transferred (e.g., flow through at least one conduit, which in an embodiment can be achieved via gravity) to a pre-treatment system 70 to be pretreated as described herein.
  • the type of pre-treatment can depend upon the algae and the algae product. For example, chemical treatment, ozone, low concentration of bleach, an acid or a base can be used to stress the algae to induce oil formation in the second algae cultivation stage.
  • the algae is mixed with a chemical in a tank for a short period of time (e.g., less than 1 hour) prior to algae flowing or otherwise being transferred to the second cultivation stage 80 and dilution in the second stage media.
  • the rinsed, concentrated algae slurry can flow or otherwise be transferred to second algae cultivator or cultivation stage 80 (e.g., flowing the rinsed concentrated algae slurry through at least one conduit, which in an embodiment can be achieved via gravity or pump 71), where additional algae can be cultivated in a second cultivation stage media, which can be different from the first cultivation stage media.
  • the second cultivator or cultivation stage 80 also includes one or more algae cultivation devices 80a, 80b, 80c, such as an open raceway, a closed photobioreactor, a combination of open raceways and closed photobioreactors, a heterotrophic reactor, or any other suitable algae cultivation devices.
  • algae cultivation devices 80a, 80b, 80c such as an open raceway, a closed photobioreactor, a combination of open raceways and closed photobioreactors, a heterotrophic reactor, or any other suitable algae cultivation devices.
  • the second stage media containing the additional algae can flow or otherwise be transferred (e.g., flowing the additional algae through at least one conduit, which in an embodiment can be achieved via gravity or pump 81) from second cultivation stage 80 to another or second hollow fiber dead-end filtration system 50b, such as one or more of the hollow fiber dead-end filtration systems described herein including the multistage systems of Figs. 6 and 7.
  • a recycled media hold-up reservoir 83 like the reservoir 63 in the first cultivation stage 60, can be in fluid communication with hollow fiber dead-end filtration system 50b, and can be used to store the recycled media until the recycled media is needed in the second cultivation stage 80.
  • the permeate from second filtration system 50b can flow or otherwise be transferred from filtration system 50b to reservoir 83 through at least one conduit.
  • the concentrated algae slurry product obtained from dead end filtration system 50b can be rinsed according to any rinsing method or sequence described herein prior to removal of the concentrated algae through an outlet or conduit 84.
  • the permeate obtained during the rinsing can either be added to the second stage recycled media or discharged from the system.
  • Rinsing can be performed by stopping the liquid in-feed to the filtration system (or stopping the last stage of filtration in a multi-stage filtration system), and feeding water or other suitable rinsing solution to the system to displace the second cultivation stage media.
  • the permeate recovered during the rinsing can be added to the second stage recycled media or discharged from the system.
  • the permeate obtained from hollow fiber dead-end filtration system 50b that is stored in a recycled media hold-up reservoir 83 can be stored until the media is needed in a packed bed absorber 86.
  • the recycled media can flow or otherwise be transferred from reservoir 83 to packed bed absorber 86 (e.g., flowing the recycled media through at least one conduit, which in an embodiment can be achieved via gravity or pump 85).
  • the recycled media can flow through absorber 86 (e.g., via gravity) where the media contacts a gas containing carbon dioxide in the absorber 86, and sodium carbonate in the media can be converted to sodium bicarbonate resulting in a carbonated media.
  • the carbon dioxide containing gas can enter absorber 86 through a gas inlet or conduit 88, which in an embodiment can be located at the bottom of packed bed absorber 86.
  • the carbon dioxide absorbed by the recycled media in absorber 86 reduces the concentration of carbon dioxide in the gas.
  • the carbon dioxide depleted gas can exit absorber 86 through a gas outlet or conduit 89, which in an embodiment can be located at the top of absorber 86.
  • the carbonated media can flow or otherwise be transferred from absorber 86 to a storage carbonate media hold-up reservoir 87 (e.g., via the fluid flowing through at least one conduit, which in an embodiment can be achieved via gravity).
  • the reservoir 87 can be covered with a carbon dioxide retaining lid or cover so that the carbon dioxide does not escape into the atmosphere.
  • the carbonated media can flow or otherwise be transferred from the carbonated media hold-up reservoir 67 back to second algae cultivator or cultivation stage 80 (e.g., via flowing the carbonated media through at least one conduit, which in an embodiment can be achieved via gravity or pump 82).
  • any conduit between the hold-up reservoir 87 and algae cultivator 80 can be enclosed so that the carbon dioxide does not escape to the atmosphere. Examples of enclosed conduits include a pipe or a covered, lined aqueduct.
  • the absorber 86 can include multiple packed bed columns instead of a single packed bed column. If multiple packed bed columns are used, the gas and liquid fluid can flow through the columns in series or in parallel.
  • each of the algae harvesting and cultivation systems and methods illustrated by the embodiments of Figs. 10 to 15 can include one or more controller, which can be programmed or configured to operate with one or more of the system components so as to perform various functions of the system including valving, cultivating, harvesting, pumping, backwashing, rinsing, filtration, permeate flow, chemical cleaning, storing, flowing or any other system functions.
  • the one or more controller can include at least one processor and at least one memory device which stores instructions, which when executed by the at least one processor, cause the at least one processor to operate with any of the system components.
  • the systems of Figs. 10 to 15 can include at least one input device and/or at least one display device, and the one or more controller can be programmed or configured to operate with the at least at least one input device and/or at least one display device.
  • Fig. 16 is a schematic diagram illustrating an embodiment of a hollow fiber dead-end filtration system of the present disclosure in which multiple modules are connected or coupled fluidly in parallel within a cassette, and in which backwash, filtration and other systems operations can be performed through a single set of valves.
  • the example illustrated in Fig. 16 includes a single cassette 56 having forty-eight modules 11.
  • Modules 11 are structured and arranged to be held or positioned in at least one treatment tank (according to any of the one or more treatment tanks described herein), and thus cassette 56 is also positioned or held in the at least one treatment tank.
  • Each of the forty-eight modules 11 is connected fluidly in parallel via a cassette header 56.
  • the entire cassette 56 can perform filtration, backwash, and other system functions such as cleaning through a single set of permeate and backwash valves 25 and 21, respectively (e.g., only one permeate valve and only one backwash valve). That is, a backwash sequence and a dead-end filtration process can be performed via opening and closing permeate and backwash valves 25 and 21.
  • the system of Fig. 16 includes at least one treatment tank and a cassette positioned in the treatment tank.
  • the cassette includes a plurality of membrane filtration modules 11 coupled fluidly in parallel via a cassette header 56.
  • the number of modules can be 48 or more.
  • Each of the plurality of membrane filtration modules 11 includes hollow fiber membranes defining lumens, and the total outside surface area of all of the hollow fiber membranes of the cassette 56 in an embodiment can range from 500 m 2 to 2200 m 2 .
  • a single permeate valve 25 e.g., only one permeate valve
  • a single backwash valve 21 e.g., only one backwash valve
  • the system is configured to perform dead-end filtration of an algae slurry contained in the at least one treatment tank so that permeate is pulled through pores of the hollow fiber membranes and flows inside the lumens of the hollow fiber membranes and retentate is produced outside the lumens of the hollow fiber membranes.
  • the system is also configured to perform a backwash sequence in which a backwash fluid (e.g., at least one of a fluid and a gas) flows inside the lumens of the hollow fiber membranes and is pushed through the pores of the hollow fiber membranes so as to remove any foulants that have accumulated on the hollow fiber membranes.
  • a backwash fluid e.g., at least one of a fluid and a gas
  • the single backwash valve for the backwash sequence can have an actuation time of three seconds or less, and the actuation time for the singe backwash valve can include the time to open or close the single backwash valve.
  • the single permeate valve for the backwash sequence can have an actuation time of three seconds or less, and the actuation time for the singe permeate valve can include the time to open or close the single permeate valve.
  • Fig. 17 is a schematic diagram illustrating an embodiment of a hollow fiber dead-end filtration system of the present disclosure in which multiple cassettes having modules are connected or coupled fluidly in parallel in a bank, and in which backwash, filtration and other system operations can be performed through a single set of valves.
  • the example illustrated in Fig. 17 includes four cassettes 56, each of which has sixteen modules 11.
  • Modules 11 are structured and arranged to be held or positioned in at least one treatment tank (as described herein), and thus each of cassettes 56 is also positioned or held in the at least one treatment tank.
  • Each cassette 56 is connected or coupled fluidly in a single bank 55, which bank 55 is therefore also structured and arranged to be held in the at least one treatment tank.
  • Each module 11 is connected or coupled fluidly in parallel via a cassette header 56.
  • Each cassette 56 is connected fluidly in parallel via a bank header 54.
  • the entire bank 55 can perform filtration, backwash, and other system functions such as cleaning through a single set of permeate and backwash valves 25 and 21, respectively. That is, a backwash sequence and dead-end filtration process can be performed via opening and closing backwash valves 25 and 21.
  • Each of the cassettes 56 can be isolated from the permeate 25 and backwash 21 valves for maintenance, cleaning, or other operations by closing isolation valve 53.
  • the system of Fig. 17 includes at least one treatment tank and a bank positioned inside the at least one treatment tank.
  • the bank includes at least a first cassette and a second cassette.
  • the first and second cassettes are coupled fluidly in parallel via a bank header.
  • the first cassette includes a first plurality of membrane filtration modules coupled fluidly in parallel via a first cassette header.
  • the second cassette includes a second plurality of membrane filtration modules coupled fluidly in parallel via a second cassette header.
  • Each of the first and second plurality of plurality of membrane filtration modules include hollow fiber membranes defining lumens.
  • the total outside surface area of all of the hollow fiber membranes of the bank in one embodiment can range from 500 m 2 to 10,000 m 2 .
  • the system further includes a single permeate valve (e.g., only one permeate valve) coupled fluidly to the bank header, and a single backwash valve (e.g., only one backwash valve) coupled fluidly to the bank header.
  • the system is configured to (a) perform dead-end filtration of an algae slurry contained in the at least one treatment tank by pulling permeate through pores of the plurality hollow fiber membranes and flows inside the lumens of the hollow fiber membranes and retentate is produced outside the lumens of the hollow fiber membranes, and (b) perform a backwash sequence in which a backwash fluid (e.g., at least one of a fluid or a gas) flows inside the lumens of the hollow fiber membranes and is pushed through the pores of the plurality of hollow fiber membranes so as to remove any foulants that have accumulated on the hollow fiber membranes.
  • a backwash fluid e.g., at least one of a fluid or a gas
  • the single backwash valve for the backwash sequence can have an actuation time of three seconds or less, and the actuation time can include the time to open or close the single backwash valve.
  • the single permeate valve for the backwash sequence can have an actuation time of three seconds or less, and the actuation time can include the time to open or close the single permeate valve.
  • each of systems and methods illustrated by the embodiments of Figs. 16 and 17 can also include one or more controller, which can be programmed or configured to operate with one or more of the system components so as to perform various functions of the system including cultivating, harvesting, valving, pumping, backwashing, rinsing, filtration, permeate flow, chemical cleaning, storing, flowing or any other system functions.
  • the one or more controller can include at least one processor and at least one memory device which stores instructions, which when executed by the at least one processor, cause the at least one processor to operate with any of the system components. It should additionally be appreciated that certain embodiments the systems of Figs.
  • any suitable hollow fiber membranes, cassette and/or modules having such hollow fiber membranes can be utilized in any one or more of the filtration systems of the present disclosure.
  • commercially available and suitable cassettes and/or modules having hollow fiber membranes include ZeeWeedTM ultra filter technologies including ZW 500D modules and ZW 500 Cassettes.
  • one or more concentration sensor can be included in any the systems described herein.
  • one or more concentration sensor can be included in one or more of tanks or stages (including the earthen lined tank), and one or more conduit so that the system can, for example, determine whether concentration of the in-feed, algae or biological slurry and/or the retentate has reached or attained a predetermined or specified level.
  • a predetermined or specified level can be determined by sensing the concentration using one or more concentration sensor or by knowing the volumetric flow rate.
  • high concentration solid slurries e.g., 0.5% to 2%) can be attained using short backwash intervals (e.g., three minutes or less), and shorter backwash off-line periods, and with minimal energy input.
  • a hollow-fiber dead-end membrane system was operated utilizing a reversing flow pump as illustrated in Fig. 2 so as to filter a 0.08% Chlorella sp. slurry from an open raceway algae cultivation system.
  • the flow pump was fast acting, so the backwash off-line period was only one second longer than the backwash flow period.
  • the system was initially operated under a ten second backwash off-line period and a 15 minute backwash interval.
  • VCF volumetric concentration factor
  • the dead end filtration system of the present disclosure required 0.04 kWh/m 3 to 0.16 kWh/m 3 of energy to obtain such high concentrations of solids algae, while a ceramic cross-flow filtration system utilizing the same algae and media required significantly more energy - 4 to 7 kWh/m 3 .
  • a shorter backwash period e.g., three seconds or less
  • a very short backwash interval e.g., one minute
  • a dead-end hollow fiber filtration system was operated with a reversing flow pump as illustrated in Fig. 2 to filter a 0.08% Chlorella sp. slurry to high concentration, e.g., greater than 3%, from an open raceway algae cultivation system.
  • the pump was again fast acting, so the backwash off-line period was only one second longer than the backwash flow period.
  • the final VCF of 15 was achieved, i.e., the final retentate algae concentration was 1.2%, which was generally expected for non-flocculated biological slurries.
  • a final VCF of 225 was achieved, i.e., the final retentate algae concentration was 18%. It was therefore illustrated that using a short backwash interval, such as one minute, with a short backwash period, such as three seconds, resulted in a 15-fold improvement in the final concentration attained with a hollow fiber dead-end membrane system.
  • the dead end filtration system required 0.04 to 0.16 kWh/m 3 of energy to obtain such high concentrations of solids algae, while a ceramic cross-flow filtration system utilizing the same algae and media required significantly more energy - 4 to 7 kWh/m 3 .
  • Table 1 below provides a comparison of the average flux for different system configurations to concentrate algae slurries based upon a permeability concentration curve for Chlorella sp. with a one minute backwash interval and a three second backwash off-line period.
  • the total membrane area is the same, but the configuration is different, i.e., all in one stage (single stage), equally divided among multiple stages (equal area multistage), and decreasing area in each successive stage (decreasing area multistage).
  • Another difference in the configuration is the operational control, i.e., the same flux in each stage (i.e., the same or substantially the same constant flux), or variable flux in each stage, independent of the other stages (i.e., variable flux).
  • the equal area and variable flux two-stage system For a very low concentration algae slurry, i.e., 0.02 g/l, concentrated to 10% suspended solids, the equal area and variable flux two-stage system has twice the throughput of a single stage system or an equal area, constant flux multistage system. Similarly, for a low concentration algae slurry, i.e., 0.02 g/l, concentrated to 10% suspended solids, the variable area and variable flux three-stage system has triple the throughput of a single stage system or an equal area, constant flux multistage system. A decreasing area, variable flux three-stage system provides a 15% throughput improvement over a decreasing area, variable flux two stage system.
  • a decreasing area and variable flux to multistage system has a greater impact on throughput.
  • a variable flux, decreasing area two-stage system has six times the throughput of a single stage system or equal area, constant flux multistage system.
  • a decreasing area, variable flux three-stage system has a 25% higher throughput than a decreasing area, variable flux two-stage system.
  • a three-stage variable flux hollow fiber dead-end filtration system configured according to the embodiment of Fig. 7 was used to harvest and dewater an approximately 0.05% Nannochloropsis sp. slurry.
  • a backwash off-line period of three seconds was used, and the backwash valve actuation time was approximately 0.25 seconds.
  • the backwash flow started immediately since the gravity backwash system of Fig. 7 was used, so the backwash flow period was 2.5 seconds.
  • a final retentate concentration of 15% was achieved by using a backwash interval of one minute in the first two stages and thirty seconds in the third stage.
  • the advantage of using a purge valve to increase the acceptable flux range while increasing the throughput or reducing the energy consumption is illustrated.
  • Table 2 below compares the flux range for three example hollow fiber dead-end filtration systems: (1) a system configured according to the embodiment of Fig. 5; (2) a system configured according to the embodiment of Fig. 5 with the purge valve 26 eliminated; and (3) a system configured according to the embodiment of Fig 4.
  • the permeate conduit is sized for minimal pressure drop.
  • System 1 and System 2 there is no purge valve, so the permeate conduit is sized so that air is entrained in the liquid permeate flow and removed from the conduit.
  • the height between the liquid in treatment tank 10 and permeate level in permeate siphon tank 41 is such that a seven p.s.i. suction or pulling force is used on the membranes at no flow.
  • the system maintains 6 p.s.i. ( ⁇ 1 p.s.i.) pulling or suction force across the membranes, and the pressure at the pump is reduced to maintain this pressure as flow is increased.
  • the suction pressure is lower in System 3 because some margin is needed to avoid over-pressurization as the controls adjust to changing flow; whereas in Systems 1 and 2, it is impossible to draw more suction than the change in elevation.
  • Table 3 below illustrates the cost per module as function of grouping for a 250 million gallon per day algae harvest and dewatering plant containing 10,000 modules.
  • the installed cost of small automatic valves used for individual modules (including the cost of the valve, the cost of wiring and plumbing air to the valve and the cost of controls for the valve) is assumed to be between the installed cost of a module and twice the installed cost of a module.
  • the larger valves used for groups of modules are assumed to be 50% more expensive than the smaller valves used for single modules.
  • the first column illustrates the approach of using a set of valves for each module.
  • the second column illustrates the approach of grouping a system into 20 racks of 500 modules each to minimize the number of automatic valves. In the second case, the valve actuation time is 15 seconds.
  • the third column illustrates an approach according to one embodiment of the present disclosure in which the modules are grouped into 200 cassettes of 50 modules each, such that the valve actuating time is three seconds (rather than minimizing the number of valves). It should be appreciated that Table 3 illustrates that minimizing the number of valves minimizes the cost of the filtration plant for a fixed number of modules.
  • the cost per quantity of permeate removed is more relevant than the cost of the filtration plant for a fixed number of modules.
  • Table 4 examines the cost of per quantity of permeate removed in terms of net filtration time per cycle per module divided by the module cost including valves from Table 3.
  • the full backwash flow rate is assumed to be twice the permeate flow rate during filtration, and the average backwash flow rate during the time the valves are opening and closing is assumed to be half of the full backwash flow rate.
  • the time at full backwash flow is assumed to be three seconds.
  • the backwash recovery time is the time to re-filter the permeate that was pushed back into the retentate during the backwash. Backwash intervals of four minutes and two minutes are considered for each of the three grouping options.
  • grouping modules is less costly than using a single set of valves for each module, and grouping modules so that the maximum valve actuation time is three seconds is less costly than grouping the modules to minimize the number of valves.
  • flow per module cost is 87% higher for grouping so that the maximum actuation time (e.g., the time to open or close valves) is three seconds or less compared to grouping modules to minimize the number of valves.
  • the flow per module cost is 22% higher for grouping so that the maximum actuation time is three seconds or less.
  • a two-stage cultivation and harvesting process such as the systems and methods described in Figs. 14 and 15, was used to grow Nitszchia sp. to a produce an algal lipid oil product.
  • the algae were cultivated under nutrient replete conditions during the first stage of cultivation to attain high biomass productivity.
  • lipid oil accumulation was induced by limiting the silica and nitrogen in the media.
  • this process was implemented by growing the algae in nutrient replete conditions, and then stopping the addition of nitrogen and silica in the fertilizer.
  • Another example embodiment of the present disclosure is the use of a multi-stage cultivation and harvesting method and system (e.g., the systems and methods of Figs. 13 and 14) along with a chemical trigger of caffeine.
  • Caffeine has been used as a trigger to induce a response in genetically engineered algae.
  • the concentration of caffeine required to induce the response is 100 mg/I.
  • the algae is grown without caffeine in the first stage and then caffeine is added in the second stage. If the algae are grown at 1 g/liter, then caffeine equivalent to 10% of the weight of the algae must be added in the second stage, which is prohibitively expensive.
  • the recycled media must be treated to remove the caffeine prior to re use the first stage.
  • Adding a hollow fiber dead-end filtration step after the first stage of the process, as illustrated in Figs. IB and 14, can remove all of the media so that permeate can be recycled to the first stage without treatment to remove the caffeine. Additionally, concentrating the algae to 10% in the hollow fiber dead-end filtration system and adding the caffeine to the concentrate prior to re-cultivation, can reduce the amount of caffeine required by 100-fold. Also, the media from the second stage cultivation can be recycled, so no treatment is needed to remove caffeine that remains in the second stage media.
  • the diatom Thalassiosira weissflogii was cultivated for use in a shrimp larval feed.
  • the diatom was cultivated to approximately 0.5 g/l and the algae slurry was added to a vessel containing shrimp larva.
  • the diatom was cultivated to approximately 0.5 g/l and the algae slurry was harvested and dewatered to a 5% slurry of live diatoms in a hollow fiber dead-end filtration system configured as illustrated in Fig. 6.
  • the 5% live diatom slurry was stored at 4 ⁇ C for two weeks and then diluted to 0.5 g/l and added to a vessel containing shrimp larva.
  • the viability and health of the shrimp larva was similar for both the larva that were fed freshly grown algae as well as the larva that were fed algae that had been concentrated in a hollow fiber dead-end filtration system, stored for two weeks, and then reconstituted into dilute slurry.
  • a hollow-fiber dead end filtration system that utilizes a rinse step can reduce the dissolved solids by orders of magnitude.
  • Chlorella sp. was cultivated at 0.7 g/l in a bicarbonate/carbonate media at a pH of 9.5 and the algae were harvested using a centrifuge to attain a 15% slurry.
  • the algae needs to be processed at a pH of less than 7, which would require the addition of 125g of sulfuric acid per kilogram of algae to neutralize the dissolved bicarbonate/carbonate in the slurry prior to the extraction process.
  • a lower cost lined earthen pond can be used as a treatment tank in a multistage hollow fiber membrane filtration system, for example, as described in Fig. 6.
  • attaining a high algae concentration in a short amount of time typically requires maximizing the packing density of the hollow fiber membranes.
  • the hydraulic residence time can be much lower in multistage hollow fiber membrane filtration systems, such as the system illustrated in Fig. 6 because of the higher average flux in the first few stages, and the effect of reducing packing density is much less pronounced. For example, if the packing density is reduced from 15 ft 2 to 7.5 ft 2 of membrane area per gallon in the first two stages of a three stage system, then the residence time to achieve a 15% slurry from 0.05% concentration feed increases by 12 minutes.
  • a lower cost earthen lined pond can be used as the containment or treatment tank for one or more of the first few stages of a multistage system, or for the first stage only in a multistage system, thereby substantially decreasing the packing density without having a major impact on the algae residence time in the system.
  • Fig. 18 illustrates another non-limiting embodiment of a hollow-fiber dead filtration system of the present disclosure.
  • the system of Fig. 18 includes all of the same components described in connection with Fig. 1, as well as other components, such that those components in Fig. 18 are marked with the same element numbers as used in Fig. 1.
  • the description of those elements including each of the alternatives discussed in connection with Fig. 1 apply in many respects to like element numbers in Fig. 18.
  • the system of Fig. 18, like the system of Fig. 1, includes a treatment tank 10 structured and arranged to receive and treat a liquid feed containing suspended solids (e.g., a biological slurry or algae slurry/feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve) to produce filtered permeate substantially free of suspended solids and a retentate with a suspended solids content higher than the liquid feed.
  • a plurality of submerged hollow fiber membranes 12 are contained or held within treatment tank 10.
  • the submerged hollow fiber membranes 12 can be arranged into one or more module 11 that is contained in treatment tank 10.
  • the one or more module 11 can also be arranged into one or more cassette.
  • the hollow fiber membrane module 11 can include headers attached to each hollow fiber membrane 12 so as to create a watertight connection between the outside of the membranes 12 and a permeate channel of the header.
  • the outer surface of the hollow fiber membranes 12 is in contact with the liquid feed and retentate.
  • permeate is pumped or pulled through pores of the hollow fiber membranes so that the permeate is withdrawn through the inside of the lumens of the hollow fibers and retentate is produced outside the lumens of the hollow fibers (e.g., inside the permeate tank).
  • a blower 13 can push air through at least one conduit and distributer 14 to create air bubbles 15 that are released below the hollow fibers to create fluid movement and movement of the hollow fibers, which aids in reducing fouling and improving backwash efficiency.
  • the air bubbles can be released continuously, intermittently, or only during the backwash cycles.
  • permeate pump 22 a controller 29 (e.g. a programmable logic controller) controls the permeate pump 22 and control valve 44 based upon the permeate flow rate measured by flow meter 28 and the suction or negative pressure measured by pressure transducer 27.
  • Pulsation dampener 43 aids in maintaining a consistent suction or negative pressure by dampening fluctuations caused during variations in pump 22, control valve 44, and control valve 45.
  • controller 29 positions control valve 45 to simulate the flow restriction created by the withdrawal of permeate through the hollow fiber membranes 12, headers attached in membrane module 11, and control valve 44 based upon the permeate flow rate measured by flow meter 28 and the suction or negative pressure measured by pressure transducer 27 and pressure transducer 74.
  • controller 29 positions control valve 46 to apply a backwash pressure to valve 25 based upon the pressure measured by pressure transducer 39.
  • the backwashing sequence is initiated by opening valves 25 and 26, and closing valve 21.
  • Valves 23 and 24 may be closed or left open depending on the desired backwash flow profile.
  • Controller 29 positions control valve 44 and adjusts pump 22 to achieve the desired pressure profile based upon pressure transducer 27.
  • Pulsation dampener 48 aids in achieving the intended pressure during backwash by dampening fluctuation caused by opening valves 25 and 26 and closing valve 21.
  • controller 29 adjusts control valve 45 to apply a negative pressure to valve 21 based upon the pressure transducer 74.
  • Fig. 19 illustrates another non-limiting embodiment of a hollow-fiber dead filtration system of the present disclosure.
  • the system of Fig. 19 includes many of the same components described in connection with Fig. 1-5 and Fig 18. Those components in Fig. 19 are marked with the same or similar element numbers as used in Figs. 1-5 and Fig. 18. The description of those elements, including each of the alternatives discussed in connection with Figs. 1-5 and Fig. 18, apply in many respects to like element numbers in Fig. 19.
  • Pump 22 is an air-actuated diaphragm pump, e.g., a double diaphragm pump, that is started and stopped by opening and closing valve 90.
  • Pulsation dampener 43 reduces fluctuations in the suction or negative pressure used to withdraw the permeate caused by operation of the diaphragm pump.
  • a treatment tank 10 structured and arranged to receive and treat a liquid feed containing suspended solids (e.g., an algae feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve) to produce a filtered permeate substantially free of suspended solids and a retentate with a higher suspended solids content than the liquid feed.
  • the treatment tank 10 contains submerged hollow fiber membranes 12 arranged into one or more module 11, which can be arranged into one or more cassettes. In the illustrated embodiment, the submerged hollow fiber membranes 12 are arranged into a single module 11 that is contained in treatment tank 10.
  • one or more module 11 can include headers attached to each hollow fiber membrane 12 to create a watertight connection between the outside of the membranes 12 and a permeate channel of the header.
  • the outer surface of the hollow fiber membranes is in contact with the liquid feed and retentate.
  • permeate is pulled through the pores of the hollow fiber membranes so that the permeate is withdrawn through the inside of the lumens of the hollow fibers and a retentate is produce outside the lumens of the hollow fibers of the membrane.
  • the fluid level of the retentate on the outside of the hollow fiber membranes is at Elevation 1.
  • valve 21 is open, valve 25 is closed, and permeate is withdrawn through at least one conduit by pump 22.
  • Pump 22 lifts the permeate to an elevated permeate gravity feed tank 40 that is vented to the atmosphere.
  • the permeate exits the system through fluid conduit 49 connected to tank 40 at Elevation 2.
  • the elevated tank 40 may be a pipe that is similar size to the conduit exiting pump 22 or the conduit connecting tank 40 to valve 25. [00210]
  • the elevated tank 40 applies pressure to valve 25 based upon the height of the tank 40.
  • the suction pressure at the inlet of pump 22, used to withdraw permeate through the lumens, is the difference between the pressure output of pump 22 and the air pressure supplied to pump 22.
  • the height difference between Elevation 1 and Elevation 2 sets a maximum pressure output for pump 22.
  • the backwash return line from tank 40 exits at Elevation 3.
  • the height difference between Elevation 1 and Elevation 3 sets the minimum pressure output of pump 22.
  • the air pressure to pump 22 is set by adjusting the air pressure control regulator 58 based upon the pressure measurement device 59.
  • a backwashing sequence is initiated by closing valve 21 and opening valve 25.
  • valve 21 When valve 21 is closed, pump 22 will stall because liquid cannot flow.
  • the suction pressure will be maintained at valve 21 while the pump is stalled because it is an air operated diaphragm pump.
  • the pressure for the backwash is set by the height difference between Elevation 1 and the height of the fluid in the backwash tank 40.
  • Elevation 2 is higher than Elevation 3, thereby establishing an inventory for back pulsing or backwashing of the system.
  • a difference in elevation between Elevation 3 and Elevation 1 preferably is significant in order to ensure that the system always has at least some back pressure on pump 22 to avoid oversuction and potential rupture of the membranes 12.
  • Elevation 1 may be about 5 ft. above ground level
  • Elevation 2 may be about 22 ft. above ground level
  • Elevation 3 may be about 19 ft. above ground level.
  • a difference between Elevations 2 and 1 may be between about 10 ft. and about 30 ft., preferably between about 15 ft.
  • Fig. 20 illustrates another non-limiting embodiment of a hollow-fiber dead filtration system of the present disclosure.
  • the system of Fig. 20 includes many of the same components described in connection with Figs. 1-5 and Figs. 18-19, such that similar components in Fig. 20 are marked with the same or similar elements numbers as used in Figs.
  • Pump 22 moves the permeate into a permeate holding tank 20, and the permeate exits the system through conduit 49 connected to the permeate holding tank.
  • a treatment tank 10 structured and arranged to receive and treat a liquid feed containing suspended solids (e.g., an algae feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve) to produce filtered permeate substantially free of suspended solids and retentate with a higher suspended solids content than the liquid feed.
  • the treatment tank 10 contains submerged hollow fiber membranes 12 arranged into one or more module 11.
  • the one or more module 11 can also be arranged into one or more cassette.
  • the one or more module 11 in an embodiment includes headers attached to the hollow fiber membranes 12 to create a watertight connection between the outside of the membranes 12 and a permeate channel of the header.
  • the outer surface of the hollow fiber membranes 12 is in contact with the liquid feed and retentate.
  • valves 21 and 91 are open and valves 25 and 26 are closed.
  • a controller 29 e.g. a programmable logic controller
  • Pulsation dampener 43 aids in maintaining a consistent suction or negative pressure by dampening fluctuations caused during variations in pump 22 and control valves 44 and 50.
  • controller 29 positions control valve 45 to simulate the flow restriction created by the withdrawal of permeate through the hollow fiber membranes 12, headers attached in membrane module 11, and control valve 44 based upon the based upon the permeate flow rate measured by flow meter 28 and the suction or negative pressure measured by pressure transducer 27 and pressure transducer 74.
  • pump 30 is operated to withdraw permeate from the permeate holding tank 20 at the flow rate for intended backwashing and to return the permeate to the permeate holding tank 20 after passing through control valve 46.
  • Controller 29 positions control valve 46 to apply a backwash pressure to valve 25 based upon the pressure measured by pressure transducer 39, such that a pressure is immediately available at valve 25 once a backwash sequence is initiated and the valve 25 is opened.
  • the backwashing sequence is initiated by opening valves 25 and 26 and closing valves 21 and 91.
  • Controller 73 adjusts pump 30 to achieve the desired pressure profile based upon pressure transducer 27.
  • Pulsation dampener 48 aids in achieving the intended pressure during backwash by dampening fluctuations caused by opening valve 25 and closing valves 21 and 91.
  • controller 29 adjusts control valve 45 to apply a negative pressure to valve 21 based upon the pressure transducer 74, e.g., to mimic drops across the membranes 12 so that the pump 22 keeps running.
  • some suction or negative pressure remains on valve 21 before and after a back pulse, and the pump 22 preferably does not change in speed before and after the back pulse.
  • Fig. 21 illustrates another non-limiting embodiment of a hollow-fiber dead filtration system of the present disclosure. As discussed in greater detail below, the system of Fig. 21 is substantially the same as the system of Fig. 20, albeit it with a stand pipe 76 that sets a pressure instead of the control valve 46 of Fig. 20. The system of Fig. 21 includes many of the same components described in connection with Figs. 1-5 and Figs. 18-20.
  • Fig. 21 Those components in Fig. 21 are marked with the same or similar elements numbers as used in Figs. 1-5 and Figs. 18- 20. The description of those elements including each of the alternatives discussed in connection with Figs. 1-5 and Figs. 18-20 apply in many respects to like element numbers in Fig. 21.
  • Pump 22 moves the permeate into a permeate holding tank 20 and the permeate exits the system through conduit 49 connected to the permeate holding tank.
  • the treatment tank 10 contains submerged hollow fiber membranes 12 arranged into one or more module 11.
  • the one or more module 11 can also be arranged into one or more cassette.
  • the one or more module 11 in an embodiment includes headers attached to the hollow fiber membranes 12 to create a watertight connection between the outside of the membranes 12 and a permeate channel of the header. The outer surface of the hollow fiber membranes 12 is in contact with the liquid feed and retentate.
  • permeate is pulled through the pores of the hollow fiber membranes so that the permeate is withdrawn through the inside of the lumens of the hollow fibers and a retentate is produce outside the lumens of the hollow fibers of the membrane (e.g., inside the treatment tank).
  • valve 21 is open and valves 25 and 26 are closed.
  • a controller 29 e.g. a programmable logic controller
  • Pulsation dampener 43 aids in maintaining a consistent suction or negative pressure by dampening fluctuations caused during variations in pump 22 and control valves 44 and 50.
  • controller 29 positions control valve 45 to simulate the flow restriction created by the withdrawal of permeate through the hollow fiber membranes 12, headers attached in membrane module 11, and control valve 44 based upon the based upon the permeate flow rate measured by flow meter 28 and the suction or negative pressure measured by pressure transducer 27 and pressure transducer 74.
  • pump BO is operated to withdrawal permeate from the permeate holding tank 20 at the flow rate for intended backwashing and to return the permeate to the permeate holding tank 20 after passing through stand-pipe 76.
  • the return leg from stand-pipe 76 exits the stand pipe at Elevation 2.
  • a backwash pressure is applied to valve 25 based upon the height of Elevation 2, such that the system may eliminate over-pressurization that otherwise may result if the pump were set too high.
  • a height for Elevation 2, or more particularly, a difference in height between Elevations 2 and 1, may be chosen so as to avoid excessive back-pressure on membranes 12.
  • a difference between about 10 feet and about 25 feet, preferably between about 10 feet and about 20 feet, more preferably between about 15 feet and about 20 feet, and in one embodiment about 17 feet may exist between Elevations 1 and 2.
  • the backwashing sequence is initiated by opening valves 25 and 26 and closing valve 21.
  • the retentate level in treatment tank 10 is Elevation 1.
  • the backwash pressure is determined by the height difference between Elevation 1 and Elevation 2.
  • Pulsation dampener 48 reduces pressure fluctuations caused by opening valve 25 and closing valve 21.
  • controller 29 adjusts control valve 45 to apply a negative pressure to valve 21 based upon the pressure transducer 74.
  • Pulsation dampener 43 aids in maintaining the intended suction or negative pressure used to withdrawal permeate by dampening fluctuations caused by opening valve 21 and closing valves 25 and 26.
  • Fig. 22 illustrates another non-limiting embodiment of a hollow-fiber dead filtration system of the present disclosure.
  • the system of Fig. 22 includes many of the same components described in connection with Figs. 1-5 and Figs. 18-21. Those components in Fig. 22 are marked with the same or similar elements numbers as used in Figs. 1-5 and Figs. 18-21. The description of those elements including each of the alternatives discussed in connection with Fig. 1-5 and Fig 18-21 apply in many respects to like element numbers in Fig. 22.
  • a treatment tank 10 structured and arranged to receive and treat a liquid feed containing suspended solids (e.g., an algae feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve) to produce a filtered permeate substantially free of suspended solids and a retentate with a higher suspended solids content than the liquid feed.
  • the treatment tank 10 contains submerged hollow fiber membranes 12 arranged into one or more module 11, which can be arranged into one or more cassette. In the illustrated embodiment, the submerged hollow fiber membranes 12 are arranged into a single module 11 that is contained in treatment tank 10.
  • one or more module 11 can include headers attached to each hollow fiber membrane 12 to create a watertight connection between the outside of the membranes 12 and a permeate channel of the header.
  • the outer surface of the hollow fiber membranes is in contact with the liquid feed and retentate.
  • permeate is pulled through the pores of the hollow fiber membranes so that the permeate is withdrawn through the inside of the lumens of the hollow fibers and a retentate is produced outside the lumens of the hollow fibers of the membrane.
  • the fluid level of the retentate on the outside of the hollow fiber membranes is at Elevation 1.
  • valve 21 is open, valves 25 and 26 are closed, and permeate is withdrawn through at least one conduit by pump 22.
  • Pump 22 moves the permeate into a permeate holding tank 20 and the permeate exits the system through conduit 49 connected to the permeate holding tank.
  • a controller 29 e.g.
  • a programmable logic controller controls the permeate pump 22 and control valves 44 and 50 based upon the permeate flow rate measured by flow meters 28 and 75 and the suction or negative pressure measured by pressure transducer 27.
  • Pulsation dampener 43 aids in maintaining a consistent suction or negative pressure by dampening fluctuations caused during variations in pump 22 and control valves 44 and 50.
  • controller 29 positions control valve 45 to simulate the flow restriction created by the withdrawal of permeate through the hollow fiber membranes 12, headers attached in membrane module 11, and control valve 44 based upon the based upon the permeate flow rate measured by flow meter 28 and the suction or negative pressure measured by pressure transducer 27 and pressure transducer 74.
  • a height for Elevation 2 or more particularly, a difference in height between Elevations 2 and 1, may be chosen so as to avoid excessive back-pressure on membranes 11.
  • a difference between about 10 feet and about 25 feet, preferably between about 10 feet and about 20 feet, more preferably between about 15 feet and about 20 feet, and in one embodiment about 17 feet may exist between Elevations 1 and 2.
  • Backwash pump 30 lifts permeate from the permeate holding tank 20 to the elevated backwash tank 40.
  • controller 73 operates pump 30 to control Elevation 2, the liquid level in the elevated backpulse tank 40, based upon the level measured by instrument 77.
  • Tank 40 is vented to the atmosphere.
  • Instrument 77 can be a pressure sensor, level switches, level sensor or any other instrument designed to determine the level of the liquid in tank 40.
  • a backwash pressure is applied to valve 25 based upon the height of Elevation 2.
  • the backwashing sequence is initiated by opening valves 25 and 26 and closing valve 21.
  • the retentate level in treatment tank 10 is Elevation 1.
  • the backwash pressure is determined by the height difference between Elevation 1 and Elevation 2.
  • controller 29 adjusts control valve 45 to apply a negative pressure to valve 21 based upon the pressure transducer 74.
  • Pulsation dampener 43 aids in maintaining the intended suction or negative pressure used to withdrawal permeate by dampening fluctuations caused by opening valve 21 and closing valves 25 and 26.
  • Fig. 23 illustrates another non-limiting embodiment of a hollow-fiber dead filtration system of the present disclosure.
  • the system of Fig. 23 includes many of the same components described in connection with Figs. 1-5 and Figs. 18-22. Those components in Fig. 23 are marked with the same or similar elements numbers as used in Figs. 1-5 and Figs. 18-22. The description of those elements including each of the alternatives discussed in connection with Figs. 1-5 and Figs. 18-22 apply in many respects to like element numbers in Fig. 23.
  • the system of Fig. 23 includes many of the same components described in connection with Figs. 1-5 and Figs. 18-22. Those components in Fig. 23 are marked with the same or similar elements numbers as used in Figs. 1-5 and Figs. 18-22. The description of those elements including each of the alternatives discussed in connection with Figs. 1-5 and Figs. 18-22 apply in many respects to like element numbers in Fig. 23.
  • a treatment tank 10 structured and arranged to receive and treat a liquid feed containing suspended solids (e.g., an algae feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve) to produce a filtered permeate substantially free of suspended solids and a retentate with a higher suspended solids content than the liquid feed.
  • the treatment tank 10 contains submerged hollow fiber membranes 12 arranged into one or more module 11, which can be arranged into one or more cassette. In the illustrated embodiment, the submerged hollow fiber membranes 12 are arranged into a single module 11 that is contained in treatment tank 10.
  • one or more module 11 can include headers attached to each hollow fiber membrane 12 to create a watertight connection between the outside of the membranes 12 and a permeate channel of the header.
  • the outer surface of the hollow fiber membranes is in contact with the liquid feed and retentate.
  • permeate is pulled through the pores of the hollow fiber membranes so that the permeate is withdrawn through the inside of the lumens of the hollow fibers and a retentate is produce outside the lumens of the hollow fibers of the membrane.
  • valve 21 is open, valves 25 and 26 are closed, and permeate is withdrawn through at least one conduit by pump 22.
  • Pump 22 moves the permeate into a permeate holding tank 20 and the permeate exits the system through conduit 49 connected to the permeate holding tank.
  • Backwash pump 30 moves permeate from the permeate holding tank 20 to the pressurized backwash tank 78 which contains a gas bladder that is compressed by the permeate.
  • a controller 73 operates pump 30 to control the pressure in the pressurized tank 78 based upon the backwash pressure measured by pressure transducer 39.
  • a backwash pressure is applied to valve 25 by the pressurized backwash tank 78.
  • a controller 29 e.g. a programmable logic controller
  • Pulsation dampener 43 aids in maintaining a consistent suction or negative pressure by dampening fluctuations caused during variations in pump 22 and control valves 44 and 50.
  • controller 29 positions control valve 45 to simulate the flow restriction created by the withdrawal of permeate through the hollow fiber membranes 12, headers attached in membrane module 11, and control valve 44 based upon the based upon the permeate flow rate measured by flow meter 28 and the suction or negative pressure measured by pressure transducer 27 and pressure transducer 74.
  • the backwashing sequence is initiated by opening valves 25 and 26 and closing valve 21.
  • the backwash pressure is determined by the pressure in tank 78.
  • controller 29 adjusts control valve 45 to apply a negative pressure to valve 21 based upon the pressure transducer 74.
  • Pulsation dampener 43 aids in maintaining the intended suction or negative pressure used to withdrawal permeate by dampening fluctuations caused by opening valve 21 and closing valves 25 and 26.
  • FIG. 24 another non-limiting embodiment of a hollow fiber filtration is illustrated in which backwash is performed via gravity, a siphoning system is used to create the suction to pull the permeate for filtration, and control loops are included to maintain the backwash pressure and the siphon suction pressure.
  • the system of Fig. 24 includes many of the same components described in connection with Figs. 1-5 and Figs. 18-23. Those components in Fig. 24 are marked with the same or similar elements numbers as used in Figs. 1-5 and Figs. 18- 23. The description of those elements including each of the alternatives discussed in connection with Figs. 1-5 and Fig. 18-23 apply in many respects to like element numbers in Fig. 24.
  • a treatment tank 10 structured and arranged to receive and treat a liquid feed containing suspended solids (e.g., an algae feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve 19) to produce a filtered permeate substantially free of suspended solids and a retentate with a higher suspended solids content than the liquid feed.
  • Treatment tank 10 contains submerged hollow fiber membranes 12 arranged into one or more modules 11, which can be arranged into one or more cassette. In the illustrated embodiment, the submerged hollow fiber membranes 12 are arranged into a single module that is contained in treatment tank 10.
  • the one or more modules 11 can include headers attached to each hollow fiber membrane 12 so as to create a watertight connection between the outside of the membranes 12 and a permeate channel of the header.
  • the outer surface of the hollow fiber membranes is in contact with the liquid feed and retentate.
  • permeate is pulled through the pores of the hollow fiber membranes so that the permeate is withdrawn through the inside of the lumens of the hollow fibers and a retentate is produce outside the lumens of the hollow fibers of the membrane.
  • Elevation 1 the liquid level in treatment tank 10 is controlled by the addition of algae slurry through valve 19.
  • valves 25 and 26 are closed, and permeate is withdrawn through at least one siphon conduit 36 into the permeate siphon tank 41.
  • the permeate siphon tank 41 is vented to the atmosphere, and the siphon conduit 36 ends below Elevation 3, the liquid level in the permeate siphon tank 41.
  • the permeate conduit 36 has a high point at valve 26 where air or other gases that come out of solution in the permeate conduit can accumulate.
  • Controller 29 operates pump 42 to control Elevation 3 based upon the liquid level measurement 79.
  • the suction pressure of the siphon is controlled by difference in height between Elevation 1 and Elevation 3.
  • Pump 42 lifts the permeate from the permeate siphon tank 41 to the permeate holding tank 20.
  • the permeate exits the system through conduit 49 connected to the permeate holding tank.
  • permeate instead of having to pump from the siphon tank 41 all the way up to the backwash tank 40 at Elevation 2, and because only a portion of the permeate is being pumped from ground up to the backwash tank 40, permeate only needs to be raised to the height of the permeate holding tank 20, thereby permitting the use of a smaller pump within the system.
  • Backwash pump 30 lifts permeate from the permeate holding tank 20 to the elevated backwash tank 40.
  • Controller 73 operates backwash pump 30 to control Elevation 2, the liquid level in the elevated backpulse tank 40, based upon the level measured by instrument 77.
  • Tank 40 is vented to the atmosphere.
  • Instrument 77 can be a pressure sensor, level switches, level sensor or any other instrument designed to determine the level of the liquid in tank 40.
  • a backwash pressure is applied to valve 25 based upon the height of Elevation 2.
  • a height difference between Elevation 2 and Elevation 1 may be substantially similar to a height difference Elevation 1 and Elevation 3.
  • that elevation difference may be between about 10 feet and about 30 feet, preferably between about 15 feet and about 25 feet.
  • the height difference between Elevation 1 and Elevation 3 may be significantly larger than the height difference between Elevation 2 and Elevation 1, as an increased degree of the former distance may lead to higher throughput.
  • the former elevation difference may fall on the larger end of the range while the latter elevation difference may fall on the lower end of the range.
  • a height difference between Elevation 1 and Elevation 3 may be between about 20 feet and about 23 feet, while Elevations 2 and 1 may be between about 15 feet and about 20 feet, and in one aspect, about 17 feet.
  • the backwashing sequence is initiated by opening valve 25 and closing valve 21.
  • the backwash pressure is determined by the difference in height between Elevation 2 and Elevation 1.
  • the backwash valve 26 is opened so that the backwash pressure pushes accumulated air or other gases and permeate through valve 26 into the permeate gas discharge conduit 47.
  • the permeate gas discharge conduit ends in the permeate discharge tank 20.
  • the permeate gas discharge conduit could end in the permeate siphon tank 41 or the permeate discharge conduit 49.
  • FIG. 25 another non-limiting embodiment of a hollow fiber filtration is illustrated in which backwash is performed via a pressurized tank, a siphoning system is used to create the suction to pull the permeate for filtration, and control loops are included to maintain the backwash pressure and the siphon suction pressure.
  • the system of Fig. 25 is substantially similar to the system of Fig. 24, although the elevated backwash tank 40 is replaced with a pressurized backwash tank 78.
  • the system of Fig. 25 includes many of the same components described in connection with Figs. 1-5 and Figs. 18-24. Those components in Fig. 25 are marked with the same or similar elements numbers as used in Figs. 1-5 and Figs. 18-24.
  • the system of Fig. 25, like the systems of Figs. 1 to 5 and Figs. 18-24 includes a treatment tank 10 structured and arranged to receive and treat a liquid feed containing suspended solids (e.g., an algae feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve 19) to produce a filtered permeate substantially free of suspended solids and a retentate with a higher suspended solids content than the liquid feed.
  • a liquid feed containing suspended solids e.g., an algae feed received, for example, from an algae source or container that is in fluid communication with tank 10 via at least one conduit operating with an in-feed valve 19
  • Treatment tank 10 contains submerged hollow fiber membranes 12 arranged into one or more modules 11, which can be arranged into one or more cassette.
  • the submerged hollow fiber membranes 12 are arranged into a single module that is contained in treatment tank 10.
  • the one or more modules 11 can include headers attached to each hollow fiber membrane 12 so as to create a watertight connection between the outside of the membranes 12 and a permeate channel of the header. The outer surface of the hollow fiber membranes is in contact with the liquid feed and retentate.
  • permeate is pulled through the pores of the hollow fiber membranes so that the permeate is withdrawn through the inside of the lumens of the hollow fibers and a retentate is produce outside the lumens of the hollow fibers of the membrane.
  • Elevation 1 the liquid level in treatment tank 10 is controlled by the addition algae slurry through valve 19.
  • valve 21 is open, valves 25 and 26 are closed, and permeate is withdrawn through at least one siphon conduit 36 into the permeate siphon tank 41.
  • the permeate siphon tank 41 is vented to the atmosphere, and the siphon conduit 36 ends below Elevation 3, the liquid level in the permeate siphon tank 41.
  • the permeate conduit 36 has a high point at valve 26 where air or other gases that come out of solution in the permeate conduit can accumulate.
  • Controller 29 operates pump 42 to control Elevation 3 based upon the liquid level measurement 79.
  • the suction pressure of the siphon is controlled by difference in height between Elevation 1 and Elevation 3.
  • Pump 42 lifts the permeate from the permeate siphon tank 41 to the permeate holding tank 20.
  • the permeate exits the system through conduit 49 connected to the permeate holding tank.
  • Backwash pump 30 moves permeate from the permeate holding tank 20 to the pressurized backwash tank 78 which contains a gas bladder that is compressed by the incoming permeate.
  • Controller 73 operates pump 30 to control the pressure in the pressurized tank 78 based upon the backwash pressure measured by pressure transducer 39. A backwash pressure is applied to valve 25 by the pressurized backwash tank 78.
  • pressure in tank 78 may be substantially similar to pressure created by a height difference between Elevation 1 and Elevation 3.
  • that elevation difference may be between about 10 feet and about BO feet, preferably between about 15 feet and about 25 feet.
  • the pressure created by the height difference between Elevation 1 and Elevation 3 may be significantly larger than the pressure in tank 78, as an increased degree of the former distance may lead to higher throughput.
  • the backwashing sequence is initiated by opening valve 25 and closing valve 21.
  • the backwash pressure is determined by the pressure in tank 78.
  • valve 26 is opened so that the backwash pressure pushes accumulated air or other gases and permeate through valve 26 into the permeate gas discharge conduit 47.
  • the permeate gas discharge conduit ends in the permeate discharge tank 20.
  • the permeate gas discharge conduit could end in the permeate siphon tank 41 or the permeate discharge conduit 49.
  • 26 illustrates another embodiment of a multistage hollow fiber dead-end filtration system of the present disclosure in which a single elevated backwash tank 40 is used to supply the backwash pressure and a single siphon tank 41 is used to generate the permeate suction pressure, but the backwash pressure and siphon suction pressure are independently controlled for each stage.
  • Fig. 26 operates in substantially the same manner as described for Fig. 6 during filtration with valves 21a, 21b, and 21c open and valves 25a, 25b, and 25c closed.
  • the liquid level in treatment tank 10 is controlled by the addition of algae slurry through valve 19. While the other filter modules are being used for filtration, each filter module 11a, lib, or 11c can be backwashed separately by opening its backwash valve 25a, 25b, or 25c and closing siphon valve 21a, 21b, or 21c.
  • the permeate siphon tank 41 is vented to the atmosphere and the siphon conduit 36 is sloped downward to the siphon tank 41 and ends below the liquid level in siphon tank 41.
  • the slope the angled portion of the siphon conduit 36 may be selected so to be steep enough to permit air within the conduit to freely travel upward through one or more of the siphon valves 21a, 21b, 21c.
  • the system of Fig. 26 includes high points for each stage at valves 26a, 26b, and 26c for accumulation of air or other gases in the suction conduit. During backwashing, the accumulated air or other gases are discharged from the permeate lines by opening valve 26a, 26b, or 26c.
  • the high points can be associated with each stage as illustrated in Fig. 26. Alternatively, a single high point could be used for multiple stages with a single valve for discharging the accumulated air or other gases. [00240] Turning now to the independent backwash pressure control of the system of Fig.
  • controllers 73a, 73b, and 73c adjust the position of flow control valves 46a, 46b, and 46c to create a flow restriction that reduces the pressure backwash pressure at filter modules 11a, lib, and 11c below the total pressure generated by the difference in height between the liquid level in the elevated backpulse tank 40 and the liquid level in the treatment tanks 10a, 10b, and 10c based upon the pressure or flow measured by pressure transducer 27a and flow meter 28a. If one stage or more stages are always operated at the full pressure, then the flow control valves do not need used. If more stages are included, then controllers, flow control valves, pressure transducers and flow meters can be added for each stage (see, e.g., pressure transducers 27b, 27c and flow meters 28b, 28c).
  • controllers 29a, 29b, and 29c adjust the position of flow control valves 44a, 44b, and 44c to create a flow restriction that reduces the suction pressure at filter modules 11a, lib, and 11c generated by the difference in height between the liquid level in the permeate siphon tank 41 and the liquid level in the treatment tanks 10a, 10b, and 10c based upon the pressure or flow measured by pressure transducer 27a and flow meter 28a. If one stage or more stages are always operated at the full pressure, then the flow control valves do not need used. If more stages are included, then controllers, flow control valves, pressure transducers and flow meters can be added for each stage (see, e.g., pressure transducers 27b, 27c and flow meters 28b, 28c).
  • Controller 29 operates pump 42 to control liquid level in siphon tank 41 based upon the liquid level measurement 79.
  • the maximum suction pressure of the siphon is controlled by difference in height between liquid level in the siphon tank and the liquid level in treatment tanks 10a, 10b, and 10c.
  • Pump 42 lifts the permeate from the permeate siphon tank 41 to the permeate holding tank 20.
  • the permeate exits the system through conduit 49 connected to the permeate holding tank.
  • the total pressure available for backwash is controlled by the difference in height of the liquid level in the elevated backwash tank 40 and the height of the liquid level in treatment tanks 10a, 10b, and 10c.
  • Controller 73 operates backwash pump 30 to control the liquid level in the elevated backwash tank 40, based upon the level measured by instrument 77.
  • Tank 40 is vented to the atmosphere.
  • Instrument 77 can be a pressure sensor, level switches, level sensor or any other instrument designed to determine the level of the liquid in tank 40.
  • a backwash pressure is applied to valves 25a, 25b, and 25c based upon the height the liquid level in the elevated backwash tank 40.
  • Controllers 29, 29a, 29b, 29c, 73, 73a, 73b, and 73c each are a control loop.
  • Each control loop can be controlled by a separate programmable logical control system or similar device; or multiple control loops can be controlled by a single programmable logical control system or similar device.
  • each treatment tank 10a, 10b, 10c in Fig. 26 is shown as being approximately the same size, it will be appreciated that the treatments tanks 10a, 10b, 10c and related surface areas of the membranes 12a, 12b, 12c of the modules contained therein may vary in size. In particular, surface areas may step down in size in progressive stages, as the concentration of algae in later stages is higher than in preceding ones, thereby requiring less fluid and less permeate needing to be removed to result in the same yield as with the earlier stages.
  • an algae harvesting system includes at least one treatment tank, at least one membrane filtration module positioned inside the at least one treatment tank, the at least one membrane filtration module including a plurality of hollow fiber membranes defining lumens, a permeate outlet in fluid connection with the inside of the lumens, a permeate suction source and a backwash supply source in fluid connection with the permeate outlet, a permeate valve that can isolate the permeate suction source from the permeate outlet, and a backwash valve that can isolate the backwash supply source from the permeate outlet.
  • the backwash supply source is configured to apply a positive backwash pressure when the backwash valve is closed, such that when the backwash valve is opened, the backwash pressure is immediately applied to the permeate outlet and lumens.
  • the permeate suction source is configured to apply a permeate suction pressure when the permeate valve is closed such that when the permeate valve is opened the negative suction pressure is immediately applied to the permeate outlet and lumens.
  • the system is configured to: (a) perform dead-end filtration of an algae slurry contained in the at least one treatment tank by pulling a substantially algae-free permeate through pores of the plurality of hollow fiber membranes so that the permeate flows inside the lumens of the plurality of hollow fiber membranes and a retentate of the algae slurry is produced outside the lumens of the plurality of hollow fiber membranes, and (b) perform a backwash sequence in which a backwash fluid flows inside the lumens of the plurality of hollow fiber membranes and is pushed through the pores of the plurality of hollow fiber membranes.
  • the algae harvesting system also may include a controller.
  • the controller may control a backwash sequence and may be configured to limit the backwash sequence to an interval of less than about three minutes between a start of one backwash cycle and a start of a next backwash cycle.
  • the algae slurry entering the at least one treatment tank is a non-flocculated algae slurry having a first concentration of suspended algae, and the retentate in at least one treatment tank has a second concentration of suspended algae that is greater than the first concentration, the second concentration equal to at least three percent.
  • the algae slurry entering the at least one treatment tank is a non-flocculated algae slurry having a first concentration of suspended algae, and the retentate in at least one treatment tank has a second concentration of suspended algae that is about fifty times greater than the first concentration.
  • the backwash supply source may include a gravity feed tank or a pressurized tank.
  • the suction supply source may include a permeate discharge in fluid communication with the gravity feed tank or pressurized tank, such that the backwash fluid is permeate fluid.
  • the system also may include a backwash return line fluidly coupled to the gravity feed tank.
  • a fluid may be raised between a first elevation comprising a fluid level of the retentate on the outside of the hollow fiber membranes and a second elevation at the backwash return line, and a difference between the second elevation and the first elevation is between about 10 feet and about BO feet, and in one example about 17 feet.
  • the permeate suction source may include a siphon tank, which may be atmospherically vented.
  • the permeate suction source also may include a siphon conduit with a purge valve at a high point to permit a release of gases that come out of solution in the conduit.
  • the purge valve may be upstream of the permeate valve and downtream of the backwash valve, so as to permit use of the backwash supply source to provide pressure to purge gases from the siphon conduit during a backwash sequence.
  • the permeate suction source includes a permeate discharge.
  • the backwash supply source may include an elevated tank containing permeate in fluid connection with the backwash valve such that a positive backwash pressure is applied at the backwash valve, a backwash pump having an inlet in fluid communication the permeate discharge and an outlet in fluid communication with the pressurized tank.
  • a pressure in the elevated tank is controlled by measuring the pressure in the tank and varying an output of the backwash pump.
  • the permeate suction source may include a permeate discharge.
  • the backwash supply source may include a pressurized tank containing a gas bladder in fluid connection with the backwash valve such that a positive backwash pressure is applied at the backwash valve.
  • a backwash pump may have an inlet in fluid communication the permeate outlet and an outlet in fluid communication with the pressurized tank.
  • a pressure in the elevated tank may be controlled by measuring the pressure in the tank and varying an output of the backwash pump.
  • the permeate suction source may include a permeate discharge to a permeate tank.
  • the backwash supply source may include a backwash pump having an inlet in fluid communication with the permeate tank and an outlet in fluid communication with the backwash valve and a recirculation conduit having pressure control means in fluid communication with the permeate tank and the backwash pump outlet.
  • the backwash supply source may be configured to apply a positive pressure at the backwash valve by controlling a flow of fluid in the recirculation conduit.
  • the pressure control means may include an elevated section of the recirculation conduit with a vent in the elevated section, such that the fluid is pumped to a fixed height to apply the positive pressure at the backwash valve. Additionally or alternatively, the pressure control means may include a control valve positioned in the recirculation conduit to apply the positive pressure at the backwash valve.
  • the permeate suction source may include an underground tank containing permeate, a vent from the underground tank to the atmosphere, a fluid connection between the permeate valve and a point below a permeate level in the underground tank, such that a siphon is generated, and a permeate pump configured to withdraw permeate from the underground tank.
  • the permeate suction source may be configured to maintain the permeate level in the underground tank by measuring the permeate level in the tank and varying a flow rate of the permeate pump, such that a negative suction pressure is maintained at the permeate valve.
  • the permeate suction source may include a permeate pump having an inlet in fluid connection with the permeate valve, a pressure measurement device between the inlet of the permeate pump and the permeate valve, and a recirculation conduit in fluid connection with the permeate pump inlet and an outlet of the permeate pump.
  • the permeate suction source may be configured to control a pressure at the permeate valve and adjust a flow in the recirculation conduit such that a negative suction pressure is applied at the permeate valve.
  • the permeate suction source also may include a permeate discharge, which may be in fluid communication with the backwash supply source, such that the backwash fluid is permeate fluid.

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  • Medicinal Chemistry (AREA)
  • Tropical Medicine & Parasitology (AREA)
  • Virology (AREA)
  • Apparatus Associated With Microorganisms And Enzymes (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Cultivation Of Seaweed (AREA)

Abstract

L'invention concerne des systèmes de récolte et de culture d'algues et des procédés de production de concentrations élevées de produit d'algues avec une énergie minimale. Dans un mode de réalisation, un système et un procédé de filtration à impasse comprennent au moins un réservoir et une pluralité de membranes à fibres creuses positionnées dans le ou les réservoirs. Un milieu d'algues est tiré à travers les membranes à fibres creuses de telle sorte qu'un rétentat et un perméat sont produits.
EP21821515.0A 2020-06-09 2021-06-09 Systèmes et procédés biologiques de récolte et de culture d'algues Pending EP4161684A1 (fr)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
US16/896,632 US11767501B2 (en) 2016-05-09 2020-06-09 Biological and algae harvesting and cultivation systems and methods
PCT/US2021/036608 WO2021252622A1 (fr) 2020-06-09 2021-06-09 Systèmes et procédés biologiques de récolte et de culture d'algues

Publications (1)

Publication Number Publication Date
EP4161684A1 true EP4161684A1 (fr) 2023-04-12

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EP (1) EP4161684A1 (fr)
AU (1) AU2021287901A1 (fr)
BR (1) BR112022025249A2 (fr)
CO (1) CO2023000072A2 (fr)
IL (1) IL298988A (fr)
MX (1) MX2022015832A (fr)
PE (1) PE20230507A1 (fr)
WO (1) WO2021252622A1 (fr)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115245700B (zh) * 2022-06-10 2023-03-24 生态环境部长江流域生态环境监督管理局生态环境监测与科学研究中心 一种浮游生物野外在线自动采集处理装置

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20020034817A1 (en) * 1998-06-26 2002-03-21 Henry Eric C. Process and apparatus for isolating and continuosly cultivating, harvesting, and processing of a substantially pure form of a desired species of algae
JP2002530188A (ja) * 1998-11-23 2002-09-17 ゼノン、エンバイロンメンタル、インコーポレーテッド 浸漬型薄膜を用いる水の濾過
US6303035B1 (en) * 1999-07-30 2001-10-16 Zenon Environmental Inc. Immersed membrane filtration process
US10462989B2 (en) * 2013-03-13 2019-11-05 Stephen K. Oney Systems and methods for cultivating and harvesting blue water bioalgae and aquaculture
EP3458182B1 (fr) * 2016-05-09 2021-11-10 Global Algae Technology, LLC Systèmes de récolte d'algues

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Publication number Publication date
WO2021252622A1 (fr) 2021-12-16
AU2021287901A1 (en) 2023-02-02
PE20230507A1 (es) 2023-03-24
IL298988A (en) 2023-02-01
BR112022025249A2 (pt) 2023-02-14
MX2022015832A (es) 2023-03-03
CO2023000072A2 (es) 2023-02-16

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