Optimization of circulation of fluid in an algae cultivation pond

Information

  • Patent Grant
  • 8752329
  • Patent Number
    8,752,329
  • Date Filed
    Friday, April 29, 2011
    13 years ago
  • Date Issued
    Tuesday, June 17, 2014
    10 years ago
  • CPC
  • US Classifications
    Field of Search
    • US
    • 119 0620R0
    • 119 001400
    • 119 0590R0
    • 119 064000
    • 119 0590S0
    • 119 060-061
    • 119 0620A0
    • 119 0620C0
    • 119 0620N0
    • 119 0620E0
    • 119 063000
    • 047 0620R0
    • 047 001400
    • 047 0590R0
    • 047 064000
    • 047 0590S0
    • 047 060-061
    • 047 0620A0
    • 047 0620C0
    • 047 0620N0
    • 047 0620E0
    • 047 063000
  • International Classifications
    • A01G31/02
    • Term Extension
      103
Abstract
Provided herein are exemplary algae cultivation ponds having the circulation of fluid optimized for such factors as decreased energy consumption, decreased predators/competitors, decreased or eliminated flow dead zones (i.e., stagnant regions), and increased algae biomass production, such as for the production of biofuels and other algae-based products.
Description
CROSS REFERENCE TO RELATED APPLICATIONS

U.S. Non-Provisional patent application Ser. No. 12/485,862 filed on Jun. 16, 2009, titled “Systems, Methods, and Media for Circulating Fluid in an Algae Cultivation Pond”is hereby incorporated by reference.


FIELD OF INVENTION

The present invention relates generally to movement of fluid in an aquaculture, and more particularly to the optimization of circulation of fluid in an algae cultivation pond.


BRIEF SUMMARY OF THE INVENTION

Provided herein are exemplary algae cultivation ponds having the circulation of fluid optimized for such factors as decreased energy consumption, decreased predators/competitors, decreased or eliminated flow dead zones (i.e., stagnant regions), and increased algae biomass production, such as for the production of biofuels and other algae-based products.


An exemplary algae cultivation pond may comprise an expansion zone and a vane within the expansion zone. A first pond bottom may underlie the expansion zone. An exterior wall may form an angle with the first pond bottom of approximately ninety to greater than one-hundred-sixty degrees. A second pond bottom adjacent to the first pond bottom may have an approximately consistent ground elevation, approximately matching a lowermost ground elevation of the first pond bottom. Additionally, the second pond bottom may extend outward from the first pond bottom. The vane in the expansion zone may extend to a point above the second pond bottom.


In a further exemplary algae cultivation pond, a first contraction zone may be associated with a turning portion and a third pond bottom. The turning portion may have an interior portion and an exterior portion, wherein the exterior of the turning portion has a ground elevation above that of a ground elevation of the interior of the turning portion. A fourth pond bottom adjacent to the first contraction zone may extend outward from the first contraction zone. An exterior wall may form an approximately ninety degree angle with the fourth pond bottom, and have a ground elevation that gradually decreases as it extends outward from the exterior wall. Additionally, a fluid circulator may be located above the fourth pond bottom.


According to yet further exemplary embodiments, a fifth pond bottom adjacent to the fourth pond bottom may extend outward from the fourth pond bottom. An interior wall may form an approximately ninety degree angle with the fifth pond bottom, and have a ground elevation that gradually decreases as it extends outward from the interior wall. A sixth pond bottom adjacent to the fifth pond bottom, may have an approximately consistent ground elevation matching a lowermost ground elevation of the fifth pond bottom. The sixth pond bottom may extend outward from the fifth pond bottom.





BRIEF DESCRIPTION OF THE DRAWINGS


FIG. 1 illustrates an exemplary algae cultivation pond in accordance with embodiments of the present invention.



FIGS. 2A-2D illustrate exemplary ground elevations for an algae cultivation pond such as the exemplary algae cultivation pond described in the context of FIG. 1.



FIGS. 3-11 illustrate various exemplary configurations for algae cultivation ponds, such as for the exemplary algae cultivation ponds described in the context of FIG. 1 and FIGS. 2A-2D.





DETAILED DESCRIPTION

Provided herein are exemplary algae cultivation ponds having the circulation of fluid optimized for such factors as decreased energy consumption, decreased predators/competitors, decreased or eliminated flow dead zones (i.e., stagnant regions), and increased algae biomass production, such as for the production of biofuels and other algae-based products.



FIG. 1 illustrates an exemplary algae cultivation pond in accordance with various embodiments of the present invention. It should be noted that FIG. 1 is not drawn to any particular scale, and that scales of exemplary embodiments may vary from that shown in FIG. 1. Shown in FIG. 1 are zones 1 through 7, with an exterior wall and an interior wall on either side of each zone forming the exemplary algae cultivation pond. Also shown in FIG. 1 is the direction of the flow of the algae cultivation fluid in the algae cultivation pond, a distal zone or end having a first contraction zone and an expansion zone, and a promixal zone or end having a second contraction zone, an expansion zone, and a jet system or a paddlewheel (“fluid circulator”). Exemplary fluid circulators and fluid circulation systems may be found in U.S. Non-Provisional patent application Ser. No. 12/485,862, filed on Jun. 16, 2009, titled “Systems, Methods, and Media for Circulating Fluid in an Algae Cultivation Pond”, which is hereby incorporated by reference.


Referring again to FIG. 1, some exemplary algae cultivation ponds may include a contraction zone, such as the exemplary first contraction zone illustrated within the distal end. In some exemplary embodiments, one or more curved guiding vanes may be placed within the first contraction zone (not shown).


According to some exemplary embodiments, guiding vanes may be made out of High Density Poly Ethylene (HDPE). According to other embodiments, vanes may be made out of any suitable material that can direct the flow of liquid. Alternatively, vanes may be made out of aluminum or any other flexible material. A frame for a vane may be built on a bottom of the algae cultivation pond, and the vane may be mounted to the frame.


For various exemplary embodiments, the design of vanes may be accomplished by conducting computational fluid dynamics (“CFD”) or by experimenting with different configurations in actual ponds. Optimal vane design results in no or little flow separation in an algae cultivation pond, and/or uniform velocity downstream of the vanes where the flow from different sections between the vanes merge to a single channel flow. The number of vanes may vary, and may depend on channel width as well as the effective angle of divergence.


In some exemplary embodiments, the contraction zone may have a turning portion, with the turning portion having an interior portion and an exterior portion. The interior of the turning portion may have a ground elevation below that of a ground elevation of the exterior of the turning portion. In an alternative embodiment, the exterior of the turning portion may have a ground elevation that approximates a ground elevation of the interior of the turning portion.


Again, with respect to FIG. 1, zone 3 shows a first pond bottom adjacent to the first contraction zone. Both an exterior wall and an interior wall may each form an angle with the first pond bottom of approximately ninety to greater than one-hundred-thirty-five degrees, in some cases reaching greater than one-hundred-sixty degrees.


Zone 4 in FIG. 1 shows a second pond bottom adjacent to the first pond bottom. The second pond bottom may have an approximately consistent (or relatively flat) ground elevation. The ground elevation may approximately match a lowermost ground elevation of the first pond bottom at zone 3. The second pond bottom at zone 4 may generally extend outward from the first pond bottom at zone 3, and represent the deepest portion of the entire algae cultivation pond.


Because zone 4 is located a significant distance away from the jet(s) and/or the paddlewheel located at zone 6, the algae cultivation fluid in zone 4 may be shallower due to the accumulated head loss, when compared to the other zones of the algae cultivation pond. Thus, the algae in the algae cultivation fluid may face increased temperature and become less productive in terms of growth and biomass production. Accordingly, zone 4 compensates for this risk by being the deepest zone within the algae cultivation pond. Zone 4 also compensates for this risk by having a constant (i.e. relatively flat) depth.


As shown in FIG. 1, some exemplary algae cultivation ponds may comprise a second contraction zone associated with a third pond bottom, such as the contraction zone shown at or near the promixal end of zone 5. Additionally, such a second contraction zone may further comprise one or more curved vanes within the contraction zone (not shown). The second contraction zone may have a turning portion, with an interior portion and an exterior portion of the turning portion. The exterior of the turning portion may have a ground elevation above that of a ground elevation of the interior of the turning portion.


With respect to the first and/or the second contraction zones, the channel width at the bottom of the throat of the contraction zone is decreased when compared to the channel width at the bottom of the algae cultivation pond in the rest of the pond (notwithstanding a second throat of a second contraction zone). A measure of the amount of the flow contraction in the throat of the contraction zone may be determined by a factor that is called the contraction ratio (“CR”). The contraction ratio is defined as:






CR
=


W
0


W
c






where W0 is the channel width at the pond bottom in zones 1 and 4, and Wc is the width of the channel in zone 6 and/or the channel width at the intersection of channels 2 and 3 at the pond bottom. Based on various designs, the contraction ratio CR may vary between approximately 1.1 and 5.0. Additionally, the contraction ratio in the distal and promixal ends may be different.


Referring again to FIG. 1, various exemplary algae cultivation ponds may further comprise a fourth pond bottom adjacent to the second contraction zone, such as that shown by the fourth pond bottom of zone 6. The fourth pond bottom may generally extend outward from the second contraction zone. Both an exterior wall and an interior wall may each form an approximately ninety to greater than one-hundred-thirty-five degree angle (in some cases reaching an angle greater than one-hundred-sixty degrees) with the fourth pond bottom. Additionally, a fluid circulator may be located above the fourth pond bottom, such as that shown by the jet system or the paddlewheel within zone 6.


In some exemplary algae cultivation ponds, a fifth pond bottom may be adjacent to the fourth pond bottom. In FIG. 1, zone 7 represents the fifth pond bottom adjacent to the fourth pond bottom of zone 6. The fifth pond bottom may extend outward from the fourth pond bottom. Both an exterior wall and an interior wall may each form an approximately ninety to greater than one-hundred-thirty-five degree angle (in some cases reaching an angle greater than one-hundred-sixty degrees) with the fifth pond bottom.


Also shown in FIG. 1 is a sixth pond bottom at zone 1. According to various exemplary algae cultivation ponds, the sixth pond bottom may be adjacent to the fifth pond bottom at zone 7. The sixth pond bottom may have an approximately consistent (or relatively flat) ground elevation. The ground elevation may approximately match a lowermost ground elevation of the fifth pond bottom at zone 7. The sixth pond bottom may extend outward from the fifth pond bottom, until it connects at or near the region illustrated and described in connection with zone 2, which is associated with a seventh pond bottom.



FIGS. 2A-2D illustrate exemplary ground elevations for an algae cultivation pond, such as the exemplary algae cultivation pond described in the context of FIG. 1.


As shown in FIGS. 2A-2D, an arbitrary reference point is selected at or above an exterior wall. Dn represents a fixed depth from the arbitrary reference point, which in some embodiments may be in the range of approximately ten to seventy centimeters. HL represents a fixed depth that may be added to Dn. HL may be added to Dn at a point “A” (located at or near the bottom of the interior wall) and/or HL may be added to Dn (located at a point “B” at or near the bottom of the exterior wall). HL is calculated to approximately represent the compensation required for the total head loss in an algae cultivation pond and in some embodiments may be in the range of approximately one to twenty-five centimeters.


In general, pond head loss may be characterized as the sum of two different losses. The first loss, known as “Friction Loss”, may be calculated based on what is known as the Manning equation:







Δ






h
f


=



n
2



U
2


l


R
h

4
/
3







where l is the total pond length, n is the Manning coefficient that depends on the pond surface quality, U is the average flow velocity in the pond, and Rh is the pond hydraulic radius that depends on the wetted cross section of the pond. The second loss, known as one time losses or local head loss for such elements as U-turns, contractions and/or diverging sections is also dependent on the average flow velocity in the algae cultivation pond and can be calculated based on the relationships which can be found in the relevant literature. In many exemplary embodiments, a jet(s) and/or a paddlewheel(s) compensates for the total head loss in an algae cultivation pond. In other words, they generate HL, which will be lost along the pond.



FIG. 2A shows an exemplary interface between zone 2 and zone 3. As shown in FIG. 2A, the water surface is relatively parallel to the pond bottom. At the same time, the pond bottom generally increases linearly or based on any other functions in ground elevation as it extends from point “A” to point “B”.



FIG. 2B shows an exemplary interface between zone 3 and zone 4. The same configuration may be observed as an exemplary interface between zone 4 and zone 5. As shown in FIG. 2B, the water surface is relatively horizontal. At the same time, the pond bottom generally remains flat in ground elevation as it extends from the interior wall at “A” to the exterior wall at “B”. In other words, the pond bottom does not change along zone 4.


Because zone 4 is located a significant distance away from the jet(s) and/or from the paddlewheel illustrated in connection with zone 6, the algae cultivation fluid in zone 4 may be moving faster than the algae cultivation fluid located in other zones of the algae cultivation pond. Since zone 4 is located significantly downstream of the flow circulating system (e.g. jet system and/or paddlewheel), the accumulated head loss in this region is the largest. Therefore, if this zone was not deeper, the flow in this region would be shallower than the rest of the algae cultivation pond, and, thus, fastest. Accordingly, zone 4 compensates for this head loss by being the deepest zone within the algae cultivation pond. This is evidenced by HL being added to Dn at “A” at or near the bottom of the interior wall, and HL being added to Dn at “B” at or near the bottom of the exterior wall.


As FIGS. 2A-2B show, the bottom elevation in zone 3 changes from its intersection with zone 2, as shown in FIG. 2A, to its intersection with zone 4, as shown in FIG. 2B. This change in elevation of point “B” along zone 3 may be linear, abrupt, or based on any arbitrary function.



FIG. 2C shows an exemplary interface between zone 5 and zone 6. The same configuration may be observed as an exemplary interface between zone 6 and zone 7, which shows that the shape of the pond bottom does not change in zone 6. As shown in FIG. 2C, the water surface is relatively parallel to the pond bottom. At the same time, the pond bottom generally increases, linearly or based on any functions, in elevation as it extends from “A” at or near the bottom of the interior wall to “B” at or near the bottom of the exterior wall.


As FIGS. 2B and 2C show, the shape of the pond bottom in zone 5 changes from a flat shape to an uneven shape along the intersection of zone 5 with zone 6. The change of pond bottom and, thus, elevation of point “B” along zone 5 may be linear, abrupt, or may be based on any arbitrary function.



FIG. 2D shows an exemplary interface between zone 7 and zone 1. The same configuration may be observed as an exemplary interface between zone 1 and zone 2, which shows that the shape of the pond bottom does not change in zone 1. As shown in FIG. 2D, the water surface is relatively horizontal. At the same time, the pond bottom generally remains flat in elevation as it extends from “A” at or near the bottom of the interior wall to “B” at or near the bottom of the exterior wall. Because zone 1 is located immediately downstream of the pond flow circulating system (e.g. jets and/or paddlewheel) located at zone 6, due to the relatively short distance that the algae cultivation fluid has moved, the accumulated head loss in this zone is relatively low. Accordingly, zone 1 does not need to compensate for this relatively little head loss by being the shallowest zone within the algae cultivation pond. This is evidenced by HL not being added to Dn at “A” at or near the bottom of the interior wall, and HL not being added to Dn at “B” at or near the bottom of the exterior wall.


As FIGS. 2C and 2D show, the shape of the pond along zone 7 changes from the shape at its intersection with zone 6 to the shape at its intersection with zone 1. The change in the elevation of point “B” along zone 7 may be made linearly, abrupt, or based on any arbitrary function.



FIGS. 3-11 illustrate various exemplary configurations for algae cultivation ponds, such as for the exemplary algae cultivation ponds described in the context of FIG. 1 and FIGS. 2A-2D.


Various embodiments of the present invention are illustrated by the accompanying figures. It will be understood that the figures are not necessarily to scale and that details (e.g., dimensions) not necessary for an understanding of the invention or that render other details difficult to perceive may be omitted. It will be understood that the invention is not necessarily limited to the particular embodiments illustrated herein.


In exemplary embodiments, an algae cultivation pond may include both a promixal end and a distal end. In further embodiments, a fluid circulator may be applied to a distal end of an algae cultivation pond to create an induced flow in the pond. In other cases, an algae cultivation pond may not have a distal end, since one or more jets and/or one or more paddlewheels are installed in both ends of the algae cultivation pond, which means that both ends are considered to be promixal ends of the algae cultivation pond. Regardless of the case, it is generally desirable to maintain the flow of algae cultivation fluid in an energy efficient fashion, so as to minimize the formation of dead zones, where algae may sediment in the bottom of the algae cultivation pond.



FIG. 5 shows an exemplary configuration for an algae cultivation pond. In particular, FIG. 5 shows a configuration similar to the configuration shown in FIG. 4, with FIG. 5 including the placement of jets issued from submerged nozzles parallel to the sidewall in order to avoid flow separation along the walls.



FIG. 6 shows another exemplary configuration for an algae cultivation pond. In particular, FIG. 6 shows the placement of vanes within a turning portion of an algae cultivation pond.


In general, separation of a flow boundary layer from a pond wall may lead to the increased generation of undesired dead zones. Flow separation may be increased by such factors as algae cultivation fluid flowing through a turning portion of an algae cultivation pond and/or algae cultivation fluid flowing through an expanding region (e.g. expanding in width) of an algae cultivation pond. As the algal fluid flows out of such parts of the algae cultivation pond, it becomes detached or separated from a side of the algae cultivation pond. Vane placement counters this tendency for flow separation, by decreasing the effective divergence angle. Such attachment increases the efficiency of the flow of algae cultivation fluid in an algae cultivation pond, and decreases the energy required (e.g. placement of extra nozzles) to maintain circulation within the algae cultivation pond.



FIGS. 7-9 show another exemplary configuration of an algae cultivation pond. In particular, FIGS. 7-9 show the placement of vanes just outside of a turning portion (i.e. throat) of an algae cultivation pond, where the pond expands and the flow diverges and the tendency for separation of the flow of the algal fluid from the sides of the pond increases. Vane placement counters this tendency for flow separation, by decreasing the divergence angle in the expansion zones.



FIGS. 10-11 show another exemplary configuration of an algae cultivation pond. In particular, FIGS. 10-11 show the placement of vanes just inside and just outside of a turning portion (i.e. throat) of an algae cultivation pond. Again, vane placement counters the tendency for flow separation, by decreasing the divergence angle in each compartment built by the vanes.


Upon reading this, it will become apparent to one skilled in the art that various modifications may be made to the algae cultivation ponds disclosed herein without departing from the scope of the disclosure. As such, this disclosure is not to be interpreted in a limiting sense but as a basis for support of the appended claims.

Claims
  • 1. An algae cultivation pond comprising: an expansion zone; anda plurality of vanes within the expansion zone, the plurality of vanes positioned lengthwise from a throat of the algae cultivation pond to at least a fully expanded point in the expansion zone of the algae cultivation pond, with a horizontal distance between each vane progressively increasing from the throat of the algae cultivation pond to the fully expanded point in the expansion zone.
  • 2. The algae cultivation pond of claim 1, further comprising: a first pond bottom underlying the expansion zone.
  • 3. The algae cultivation pond of claim 2, further comprising: an exterior wall, the exterior wall forming an angle with the first pond bottom of approximately ninety to greater than one-hundred-sixty degrees.
  • 4. The algae cultivation pond of claim 3, further comprising: a second pond bottom adjacent to the first pond bottom, the second pond bottom having an approximately consistent ground elevation, the ground elevation approximately matching a lowermost ground elevation of the first pond bottom, and the second pond bottom extending outward from the first pond bottom.
  • 5. The algae cultivation pond of claim 4, wherein the vane in the expansion zone extends to a point above the second pond bottom.
  • 6. The algae cultivation pond of claim 5, further comprising: a first contraction zone associated with a turning portion and a third pond bottom, the turning portion having an interior portion of the pond bottom and an exterior portion of the pond bottom, wherein the exterior portion of the pond bottom of the turning portion has a ground elevation above that of a ground elevation of the interior portion of the pond bottom of the turning portion.
  • 7. The algae cultivation pond of claim 6, further comprising: a fourth pond bottom adjacent to the first contraction zone, the fourth pond bottom extending outward from the first contraction zone;an exterior wall, the exterior wall forming an approximately ninety degree angle with the fourth pond bottom, the exterior wall having a ground elevation that gradually decreases as it extends outward from the exterior wall; anda fluid circulator above the fourth pond bottom.
  • 8. The algae cultivation pond of claim 7, further comprising: a fifth pond bottom adjacent to the fourth pond bottom, the fifth pond bottom extending outward from the fourth pond bottom;an interior wall, the interior wall forming an approximately ninety degree angle with the fifth pond bottom, the interior wall having a ground elevation that gradually decreases as it extends outward from the interior wall.
  • 9. The algae cultivation pond of claim 7, wherein the fluid circulator is a jet.
  • 10. The algae cultivation pond of claim 7, wherein the fluid circulator is a paddle wheel.
  • 11. The algae cultivation pond of claim 8, further comprising: a sixth pond bottom adjacent to the fifth pond bottom, the sixth pond bottom having an approximately consistent ground elevation, the ground elevation approximately matching a lowermost ground elevation of the fifth pond bottom, and the sixth pond bottom extending outward from the fifth pond bottom.
  • 12. The algae cultivation pond of claim 6, wherein the turning portion approximates a “U” configuration.
  • 13. The algae cultivation pond of claim 12, further comprising: at least one vane placed within the “U” configuration.
  • 14. The algae cultivation pond of claim 13, wherein the vane is configured to approximate a shape of the “U” configuration.
  • 15. The algae cultivation pond of claim 6, wherein the first contraction zone has a neck or a throat.
  • 16. The algae cultivation pond of claim 6, wherein the first contraction zone has a width.
  • 17. The algae cultivation pond of claim 16, wherein the width increases after the neck or the throat of the contraction zone.
  • 18. The algae cultivation pond of claim 17, wherein a pond bottom elevation increases as the width increases.
  • 19. The algae cultivation pond of claim 1, wherein the pond is in a raceway configuration.
  • 20. The algae cultivation pond of claim 1, wherein the pond is in a serpentine configuration.
US Referenced Citations (124)
Number Name Date Kind
1926780 Lippincott Sep 1933 A
3220706 Valdespino Nov 1965 A
3468057 Buisson et al. Sep 1969 A
3897000 Mandt Jul 1975 A
3955318 Hulls May 1976 A
4003337 Moore Jan 1977 A
4115949 Avron et al. Sep 1978 A
4217728 Shimamatsu et al. Aug 1980 A
4267038 Thompson May 1981 A
4365938 Warinner Dec 1982 A
4535060 Comai Aug 1985 A
4658757 Cook Apr 1987 A
4813611 Fontana Mar 1989 A
5105085 McGuire et al. Apr 1992 A
5130242 Barclay Jul 1992 A
5227360 Sherba et al. Jul 1993 A
5338673 Thepenier et al. Aug 1994 A
5353745 Fahs, II Oct 1994 A
5478208 Kasai et al. Dec 1995 A
5518990 Ushio et al. May 1996 A
5527456 Jensen Jun 1996 A
5539133 Kohn et al. Jul 1996 A
5564630 Giles et al. Oct 1996 A
5573669 Jensen Nov 1996 A
5658076 Crump et al. Aug 1997 A
5658767 Kyle Aug 1997 A
5823781 Hitchcock et al. Oct 1998 A
5871952 Ghirardi et al. Feb 1999 A
6000551 Kanel et al. Dec 1999 A
6117313 Goldman et al. Sep 2000 A
6166231 Hoeksema Dec 2000 A
6192833 Brune et al. Feb 2001 B1
6372460 Gladue et al. Apr 2002 B1
6447681 Carlberg et al. Sep 2002 B1
6524486 Borodyanski et al. Feb 2003 B2
6579714 Hirabayashi et al. Jun 2003 B1
6626738 Shank Sep 2003 B1
6736572 Geraghty May 2004 B2
6750048 Ruecker et al. Jun 2004 B2
6831040 Unkefer et al. Dec 2004 B1
6871195 Ryan et al. Mar 2005 B2
6896804 Haerther et al. May 2005 B2
6944013 Yang Sep 2005 B2
7333195 Krei.beta et al. Feb 2008 B2
7381326 Haddas Jun 2008 B2
7391608 Tsai Jun 2008 B2
7669780 Sugano et al. Mar 2010 B2
7682821 Woods et al. Mar 2010 B2
7748650 Sloan Jul 2010 B1
7770322 Huntley et al. Aug 2010 B2
8143051 Weissman et al. Mar 2012 B2
8507254 Abuhasel Aug 2013 B1
20020105855 Behnke et al. Aug 2002 A1
20030038566 Qiu Feb 2003 A1
20030116502 DeBusk et al. Jun 2003 A1
20030140021 Ryan et al. Jul 2003 A1
20030199490 Antoni-Zimmermann et al. Oct 2003 A1
20040121447 Fournier Jun 2004 A1
20040161364 Carlson Aug 2004 A1
20040262219 Jensen Dec 2004 A1
20050064577 Berzin Mar 2005 A1
20050095569 Franklin May 2005 A1
20050164192 Graham et al. Jul 2005 A1
20050170479 Weaver et al. Aug 2005 A1
20050181345 Bradbury et al. Aug 2005 A1
20050260553 Berzin Nov 2005 A1
20050273885 Singh et al. Dec 2005 A1
20060031087 Fox et al. Feb 2006 A1
20060044259 Hotelling et al. Mar 2006 A1
20060045750 Stiles Mar 2006 A1
20060122410 Fichtali et al. Jun 2006 A1
20060155558 Corpening Jul 2006 A1
20060166243 Su et al. Jul 2006 A1
20060192690 Philipp Aug 2006 A1
20070115626 Peng et al. May 2007 A1
20070155006 Levin Jul 2007 A1
20070289206 Kertz Dec 2007 A1
20080118964 Huntley et al. May 2008 A1
20080120749 Melis et al. May 2008 A1
20080155888 Vick et al. Jul 2008 A1
20080155890 Oyler Jul 2008 A1
20080160488 Younkes et al. Jul 2008 A1
20080160591 Willson et al. Jul 2008 A1
20080160593 Oyler Jul 2008 A1
20080220486 Weiss Sep 2008 A1
20080293132 Goldman et al. Nov 2008 A1
20090011492 Berzin Jan 2009 A1
20090029445 Eckelberry et al. Jan 2009 A1
20090061928 Lee et al. Mar 2009 A1
20090126265 Rasmussen et al. May 2009 A1
20090137031 Hirabayashi May 2009 A1
20090148931 Wilkerson et al. Jun 2009 A1
20090151241 Dressler et al. Jun 2009 A1
20090162919 Radaelli et al. Jun 2009 A1
20090186860 Huff et al. Jul 2009 A1
20090234146 Cooney et al. Sep 2009 A1
20090319338 Parks et al. Dec 2009 A1
20090325270 Vick et al. Dec 2009 A1
20100022393 Vick Jan 2010 A1
20100068772 Downey Mar 2010 A1
20100100520 Dargue et al. Apr 2010 A1
20100170149 Keeler et al. Jul 2010 A1
20100170150 Walsh, Jr. Jul 2010 A1
20100183744 Weissman et al. Jul 2010 A1
20100196995 Weissman et al. Aug 2010 A1
20100198659 Meltzer et al. Aug 2010 A1
20100210003 King et al. Aug 2010 A1
20100257781 Batty et al. Oct 2010 A1
20100260618 Parsheh et al. Oct 2010 A1
20100261922 Fleischer et al. Oct 2010 A1
20100314324 Rice et al. Dec 2010 A1
20100323387 Bailey et al. Dec 2010 A1
20100325948 Parsheh et al. Dec 2010 A1
20100327077 Parsheh et al. Dec 2010 A1
20110016773 Nichols et al. Jan 2011 A1
20110023360 Ryan et al. Feb 2011 A1
20110051354 Fan et al. Mar 2011 A1
20110136212 Parsheh et al. Jun 2011 A1
20110197306 Bailey et al. Aug 2011 A1
20110258915 Subhadra Oct 2011 A1
20110287531 Hazlebeck Nov 2011 A1
20110287544 Berzin et al. Nov 2011 A1
20120252104 Waibel et al. Oct 2012 A1
20130130909 Vick et al. May 2013 A1
Foreign Referenced Citations (24)
Number Date Country
102164492 Aug 2011 CN
102348793 Feb 2012 CN
102459585 May 2012 CN
102575221 Jul 2012 CN
2427551 Mar 2012 EP
1168381 Dec 2012 HK
JOURNAL522012 Dec 2012 IN
JOURNAL122013 Mar 2013 IN
JOURNAL202013 May 2013 IN
JOURNAL372013 Sep 2013 IN
09173050 Jul 1997 JP
20110000934 Jul 2011 MX
2011008222 Jan 2012 MX
WO2004106238 Dec 2004 WO
WO2009037683 Mar 2009 WO
WO2009149519 Dec 2009 WO
WO2010008490 Jan 2010 WO
WO2010011335 Jan 2010 WO
WO2010090760 Aug 2010 WO
WO2010129041 Nov 2010 WO
WO2010147648 Dec 2010 WO
WO2011002487 Jan 2011 WO
WO2012149214 Nov 2012 WO
WO2012170737 Dec 2012 WO
Non-Patent Literature Citations (77)
Entry
Dodd, “Elements of pond design and construction.” CRC Handbook of microalgal mass culture, Richmond, ed., Boca Raton, Fl.: CRC Press, 1986, p. 265-283, see entire document, especially Fig. 1; p. 268, para 3 to p. 269, para 1; p. 270, para 1.
Santin-Montanya, I. “Optimal Growth of Dunaliella primolecta in Axenic Conditions to Assay Herbicides,” Chemosphere, 66, Elsevier 2006, p. 1315-1322.
Felix, R. “Use of the cell wall-less alga Dunaliella bioculata in herbicide screening tests,” Annals of Applied Biology, 113, 1988, pp. 55-60.
Janssen, M. “Phytosynthetic efficiency of Dunaliella tertiolecta under short light/dark cycles,” Enzyme and Microbial Technology, 29, 2001, p. 298-305.
Saenz, M.E., “Effects of Technical Grade and a Commercial Formulation of Glyphosate on Algal Population Growth,” Bulletin of Environmental Contamination Toxicology, 1997, 59: pates 638-644.
Christy et al., “Effects of Glyphosate on Growth of Chlorella,” Weed Science, vol. 29, Issue 1, Jan. 1981, pp. 5-7.
Roessler et al., “Genetic Engineering Approaches for Enhanced Production of Biodiesel Fuel from Microalgae,” ACS Symposium Series; American Chemical Society, 1994, pp. 255-270.
Grima et al. “Recovery of Microalgal Biomass in Metabolites: Process Options and Economics,” Biotechnology Advances 20, 2003, pp. 491-515.
Knuckey et al. “Production of Microalgal Concentrates by Flocculation and their Assessment as Aquaculture Feeds,” Aquacultural Engineering 35, 2006, pp. 300-313.
Applying [online] retrieved from: http://www.merriam-webster.com/dictionary/applying, on May 21, 2011; 3 pages.
Cohen, “Chemicals from MicroAlgae”, 1999, CRC Press, pp. 49 and 51.
Kureshy et al., “Effect of Ozone Treatment on Cultures of Nannochloropsis oculata, Isochrysis galbana, and Chaetoceros gracilis,” Journal of the World Aquaculture Society, 1999, 30(4), pp. 473-480.
Liao et al. “An Overview of Live Feeds Production System Design in Taiwan,” Rotifer and Microalgae Culture Systems, Proceedings of a US-Asia Workshop, Honolulu, HI, 1991, pp. 135-150.
Kanematsu et al., “Methods to Repress the Growth of a Nannochloropsis-Grazing Microflagellate,” Nippon Suisan Gakkaishi 55, 1989, pp. 1349-1352 (English Translation).
Csogor et al., “Light Distribution in a Novel Photobioreactor-Modelling for Optimization,” Journal of Applied Phycology, vol. 13, pp. 325-333.
Janssen et al., “Enclosed Outdoor Photobioreactors: Light Regime, Photosynthetic Efficiency, Scale-Up, and Future Prospects,” Biotechnology and Bioengineering, vol. 81, No. 2, pp. 193-210, Jan. 2003.
Zittelli et al., “Mass Cultivation of Nannochloropsis Sp. in Annular Reactors,” Journal of Applied Phycology, vol. 15, pp. 107-113, Mar. 2003.
Strzepek et al., “Photosynthetic Architecture Differs in Coastal and Oceanic Diatoms,” Nature, vol. 431, pp. 689-692, Oct. 2004.
Lee et al., “Isolation and Characterization of a Xanthophyll Aberrant Mutant of the Green Alga Nannochloropsis oculata,” Marine Biotechnology, 2006, vol. 8, pp. 238-245.
NCBI entry EE109892 (Jul. 2006) [Retrieved from the Internet on Oct. 19, 2009, <http://www.ncbi.nlm.nih.gov/nucest/EE109892?ordinalops=1&itool=EntrezSystem2.Pentrez.Sequence.Sequence—ResultsPanel.Sequence—RVDocSum>].
Berberoglu et al., “Radiation Characteristics of Chlamydomonas reinhardtii CC125 and its truncated chlorophyll antenna transformants tla1, tlaX, and tla1-CW+,” International Journal of Hydrogen Energy, 2008, vol. 33, pp. 6467-6483.
Ghirardi et al., “Photochemical Apparatus Organization in the Thylakoid Membrane of Hordeum vulgare wild type and chlorophyll b-less chlorina f2 mutant,” Biochimica et Biophysica Act (BBA)—Bioenergetics, vol. 851, Issue 3, Oct. 1986, pp. 331-339 (abstract only).
Steinitz et al., “A mutant of the cyanobacterium Plectonema boryanum resistant to photooxidation,” Plant Science Letters, vol. 16, Issues 2-3, 1979, pp. 327-335 (abstract only).
Koller et al., “Light Intensity During Leaf Growth Affects Chlorophyll Concentration and CO2 Assimilation of a Soybean Chlorophyll Mutant,” Crop Science, 1974, vol. 14, pp. 779-782 (abstract only).
Shikanai et al., “Identification and Characterization of Arabidopsis Mutants with Reduced Quenching of Chlorophyll Fluorescence,” Plant and Cell Physiology, 1999, vol. 40, No. 11, pp. 1134-1142 (abstract only).
Anderson, “Algal Culturing Techniques,” 2005, p. 208.
Ben-Amotz, Ami. “Large-Scale Open Algae Ponds,” presented at the NREL-AFOSR Joint Workshop on Algal Oil for Get Fuel Production in Feb. 2008.
Ebeling et al., “Design and Operation of a Zero-Exchange Mixed-Cell Raceway Production System,” 2nd Int'l Sustainable Marine Fish Culture Conference and Workshop, Oct. 2005.
Labatut et al., “Hydrodynamics of a Large-Scale Mixed-Cell Raceway (MCR): Experimental Studies,” Aquacultural Engineering vol. 37, Issue 2, Sep. 2007, pp. 132-143.
Kizilisoley et al., “Micro-Algae Growth Technology Systems,” Presented by Selim Helacioglu, Soley Institute, 2008.
Kent BioEnergy, “Fish Farm Empties Its Ponds to Grow Algae for Biofuels,” Apr. 17, 2009 (http://www-csgc.ucsd.edu/newsroom/newsreleases/2009/algaeforbiofuls.html).
Hoyt et al., “Waves on Water Jets,” J. Fluid Mech., 1977, vol. 83, Part 1, pp. 119-127.
Mitra et al., “Optical Properties of Microalgae for Enhanced Biofuels Production,” Optics Express, Dec. 2008, vol. 16, No. 26.
Rodolphi et al., “Microalgae for Oil: Strain Selection, Induction of a Lipid Synthesis and Outdoor Mass Cultivation in a Low-Cost Photobioreactor,” Biotechnology and Bioengineering, 2008, vol. 102, No. 1, pp. 100-112.
International Search Report mailed Sep. 16, 2009 for Application No. PCT/US2009/004296, filed Jul. 24, 2009.
Written Opinion of the International Searching Authority mailed Sep. 16, 2009 for Application No. PCT/US2009/004296, filed Jul. 24, 2009.
Office Action mailed Nov. 14, 2012 in China Patent Application No. 200980138072.X, filed Jul. 24, 2009.
Official Action mailed Jul. 10, 2012 in Mexico Patent Application No. MX/a/2011/000934, filed Jul. 24, 2009.
Official Action mailed Mar. 5, 2013 in Mexico Patent Application No. MX/a/2011/000934, filed Jul. 24, 2009.
Duarte et al., “Glyphosate (GP) Effects with Emphasis on Aquatic Organisms,” Colunbia Orinoquia, ISSN: 0121-3709, pp. 70-100, 2004.
Technical Card: Glyphosate, Document filed for the Pesticide Action Network and the Alternatives Thereof, for Latin America (RAP-AL)-Communications and Administration Office, Apr. 2008.
Department of Environment, Housing and Territorial Development Ministry, Resolution (1009), published Jun. 17, 2008.
International Search Report and Written Opinion of the International Searching Authority mailed May 3, 2010 for Application No. PCT/US2010/000346, filed Feb. 4, 2010.
Patent Examination Report No. 1 mailed Jan. 9, 2013 in Australia Patent Application 2010210982, filed Feb. 4, 2010.
First Office Action mailed Nov. 5, 2012 in China Patent Application No. 201080012755.3, filed Feb. 4, 2010.
Official Action mailed Sep. 17, 2012 in Mexico Patent Application No. MX/a/2011/008222, filed Feb. 4, 2010.
International Search Report and Written Opinion of the International Searching Authority mailed Aug. 30, 2010 for Application No. PCT/US2010/001731, filed Jun. 15, 2010.
Notice on the First Office Action mailed Dec. 14, 2012 in Chinese Application No. 201080036170.5 filed Jun. 15, 2010.
International Search Report and Written Opinion of the International Searching Authority mailed Aug. 19, 2010 for Application No. PCT/US2010/001755, filed Jun. 16, 2010.
International Search Report and Written Opinion of the International Searching Authority mailed Jul. 31, 2012 for Application No. PCT/US2012/035290, filed Apr. 26, 2012.
International Search Report and Written Opinion of the International Searching Authority mailed Jul. 30, 2010 for Application No. PCT/US2010/001315, filed May 4, 2010.
First Office Action mailed Oct. 25, 2012 in China Patent Application No. 201080027531.X, filed May 4, 2010.
Extended European Search Report mailed Oct. 5, 2012 in European Patent Application 10772376.9, filed on May 4, 2010.
Polle et al., “tla1, a DNA insertional transformant of the green alga Chlamydomonas reinhardtii with a truncated light-harvesting chlorophyll antenna size,” Planta, vol. 217, No. 1, May 2003, pp. 49-59.
Lawrence et al., “Variation in Plants Regenerated from Vacuolate and Evacuolate Protoplasts,” Plant Science, vol. 50, No. 2, 1987, pp. 125-132.
Beckmann et al., “Improvement of light to biomass conversion by de-regulation of light-harvesting protein translation in Chlamydomonas reinhardtii,” Journal of Biotechnology, vol. 142, No. 1, 2009, pp. 70-77.
International Search Report and Written Opinion of the International Searching Authority mailed Aug. 16, 2012 for Application No. PCT/US2012/041425, filed Jun. 7, 2012.
European Search Report mailed Oct. 5, 2012 in European Patent Application No. 10772376.9, filed May 4, 2010.
Examination Report mailed Feb. 20, 2013 in Australian Application No. 2009274500 filed Jul. 24, 2009.
Notice on the Second Office Action mailed Jun. 20, 2013 in Chinese Application No. 201080012755.3 filed Feb. 4, 2010.
Notice on the Second Office Action mailed Jul. 5, 2013 in Chinese Application No. 201080027531.X filed May 4, 2010.
Examination Report mailed Aug. 22, 2013 in Australian Application No. 2010260530 filed Jun. 15, 2010.
First Office Action mailed Aug. 29, 2013 in Mexican Application No. MX/a/2011/013710 filed Jun. 15, 2010.
Examination Report mailed Aug. 29, 2013 in European Application No. 10772376.9 filed May 4, 2010.
Examination Report mailed Sep. 19, 2013 in Australian Application No. 2010245255 filed May 4, 2010.
Notice on the Second Office Action mailed Sep. 24, 2013 in Chinese Application No. 200980138072.X filed Jul. 24, 2009.
Zuo-Xi Ruan et al., Effects of Acute Glyphosate Exposure on the Growth and Physiology of Nostoc Sphaeroides, an Edible Cyanobacterium of Paddy Rice Fields, Acta Hydrobiologica Sinica, Jul. 2008 vol. 32, No. 4.
HCAPLUS abstract 1997; 248650 (1997).
HCAPLUS abstract 2005; 600349 (2005).
HCAPLUS abstract 2007; 1143765 (2007).
Notice on the Second Office Action mailed Oct. 24, 2013 in Chinese Application No. 201080036170.5 filed Jun. 15, 2010.
Tucker (Water Treatment, 1998, Springer, pp. 1-754).
Vinneras et al (The potential for disinfection of separated faecal matter by urea and by peracetic acid for hygienic nutrient recycling, 2003, Bioresources Technology, vol. 89, pp. 155-161).
CCAP website, f2 media recipe, 2005.
Palanichamy et al (Observations on the long term preservation and culture of the marine microalga, Nannochloropsis oculata, 2004, Journal of Marine Biology Association of India, vol. 46, pp. 98-103).
Office Action mailed Nov. 11, 2013 in Mexican Application No. MX/a/2011/000934 filed Jul. 24, 2009.
Ebeling et al., “Mixed-Cell Raceway: Engineering Design Criteria, Construction, and Hydraulic Characterization,” North American Journal of Aquaculture, 2005, 67: 193-201 (abstract only).
Related Publications (1)
Number Date Country
20120272574 A1 Nov 2012 US