Devices for selective removal of contaminants from a composition

Abstract
A device for selectively removing contaminants from a crude product mixture which includes a production reactor for producing a crude oil product mixture, the production reactor includes a lipid reservoir and an alcohol reservoir and a first organic acid removal reactor in fluid communication with the production reactor. The first organic acid removal reactor includes a first housing defining an interior volume the housing configured to receive the crude oil products and disposed within the interior volume of the removal reactor housing is metal oxide media selected from the group consisting of zirconia, alumina, hafnia and titania for removing organic acidic contaminants from the crude oil product to product a purified biodiesel fuel.
Description
FIELD OF THE INVENTION

The present invention relates to devices and methods for purifying crude product mixtures. Specifically, the invention relates to devices and methods for selectively removing contaminants, such as organic acids, from a crude product mixture.


BACKGROUND OF THE INVENTION

Many commercial production operations involve processing steps directed to the removal of byproducts or contaminants from a product mixture. An example of this occurs in the commercial process for producing soybean oil.


Soybean oil is usually produced through either a mechanical pressing process or a solvent extraction process. Various preparative steps can occur in the process including cleaning, drying and dehulling of the soybeans. After the soybeans are prepared, they can be heated in order to coagulate the soy proteins to make the oil extraction process easier. In the solvent extraction process, the soybeans are then cut into flakes which are put in percolation extractors and immersed in a solvent, such as hexane. The soybean oil is solvated by the solvent and then separated from the flakes. The solvent is then separated from the soybean oil, such as with an evaporator. The solvent free crude soybean oil is then further purified (refined). In the mechanical pressing process, the soybeans are typically crushed and pressed to yield a crude soybean oil which is then further purified.


Purification steps in both mechanical pressing processes and solvent extraction processes can include degumming (removing of phosphatides), alkali refining (washing with alkaline solution to remove free fatty acids, colorants, insoluble matter and gums) and bleaching (with activated earth or activated carbon to remove color and other impurities). The alkali refining process (sometimes referred to as caustic refining) is frequently carried out by mixing a strong base, such as sodium hydroxide, into an aqueous solution and then combining the aqueous solution and the crude soybean oil and agitating the mixture. Free fatty acids in the crude soybean oil react (saponification) with the strong base to form a soap composition which is soluble in the aqueous phase and mostly insoluble in the oil phase. The aqueous phase is then removed from the soybean oil carrying away the soap composition.


Alkali refining processes are effective for the removal of free fatty acids, but suffer from various disadvantages. First, alkali refining processes generally require the handling of very caustic strong bases, such as sodium hydroxide, creating safety issues and causing significant wear on equipment. Second, such strong bases can be relatively expensive to use.


It will be appreciated that removal of free fatty acids is a process step that is part of many other industrial production processes. By way of example, biodiesel fuel is produced through a transesterification process that converts triglycerides into fatty acid alkyl esters. This process is frequently carried out with either a strong base or strong acid. In the context of the transesterification process processed with a strong base, the fatty acids react with the strong base to form a soap composition. Unfortunately, significant amounts of fatty acids are frequently present in biological feed stocks used to make biodiesel. As such, even after the transesterification reaction takes place, there can sometimes still be significant amounts of fatty acids present in the product mixture. However, guidelines for biodiesel fuel place strict limits on the concentration of fatty acids that can be present. As such, fatty acids need to be removed from biodiesel fuel made from certain types of feedstocks.


For at least these reasons, a need exists for new devices and methods for purifying crude product mixtures. Specifically, a need exists for new devices and methods for selectively removing organic acids from a crude product mixture.


SUMMARY OF THE INVENTION

The present invention relates to devices and methods for selectively removing organic acids, such as fatty acids, from a crude product mixture. In an embodiment, the invention includes a method for removing free organic acids from a crude product mixture including contacting the crude product mixture with a metal oxide substrate, the metal oxide substrate having properties sufficient to bond with free organic acids in the crude product mixture, thereby removing free organic acids and forming a refined product mixture, and separating the refined product mixture from the metal oxide substrate.


In an embodiment, the invention includes a device for removal of free organic acids from a crude product mixture including a first housing defining an interior volume, an input port, and an output port, and metal oxide media disposed within the first housing, the metal oxide media comprising a metal oxide selected from the group consisting of zirconia, alumina, hafnia, and titania.


In an embodiment, the invention includes a method of producing a refined oil product from a plant material including mechanically pressing the plant material to separate out a crude oil product and contacting the crude oil product with a metal oxide media to remove organic acids from the crude oil product, thereby producing a refined oil product.


In an embodiment, the invention includes a system for producing a refined oil product including a mechanical press and a housing defining an interior volume, the housing configured to receive a crude oil product from the mechanical press and metal oxide media disposed within the interior volume, the metal oxide media including a metal oxide selected from the group consisting of zirconia, alumina, hafnia, and titania.


In an embodiment, the invention includes a system for producing a refined oil product including an evaporator configured to remove a solvent from a crude oil product mixture; and a housing defining an interior volume, the housing configured to receive the crude oil product mixture from the evaporator, metal oxide media disposed within the interior volume, the metal oxide media including a metal oxide selected from the group consisting of zirconia, alumina, hafnia, and titania.


In an embodiment, the invention includes a device for removal of free organic acids from a crude product mixture including a first housing defining an interior volume, an input port, and an output port; metal oxide media disposed within the first housing, the metal oxide media comprising a metal oxide selected from the group consisting of zirconia, alumina, hafnia, and titania; and a temperature control unit configured to maintain the temperature within the first housing within a first temperature range for a first period of time and within a second temperature range for a second period of time following the first period, the second range higher than the first range.


In an embodiment, the invention includes a system for producing a refined oil product including a production reactor for producing a crude oil product mixture from a lipid feedstock and an alcohol, the reactor comprising a lipid feedstock reservoir, and an alcohol reservoir; and an organic acid removal reactor in fluid communication with the production reactor, the organic acid removal reactor comprising a housing defining an interior volume, the housing configured to receive the crude oil product mixture from the production reactor, metal oxide media disposed within the interior volume of the removal reactor housing, the metal oxide media comprising a metal oxide selected from the group consisting of zirconia, alumina, hafnia, and titania.


The above summary of the present invention is not intended to describe each discussed embodiment of the present invention. This is the purpose of the figures and the detailed description that follows.





BRIEF DESCRIPTION OF THE FIGURES

The invention may be more completely understood in connection with the following drawings, in which:



FIG. 1 is a block diagram of a contaminant removal device in accordance with an embodiment of the invention.



FIG. 2 is a block diagram of a contaminant removal device in accordance with another embodiment of the invention.



FIG. 3 is a block diagram of a contaminant removal device in accordance with another embodiment of the invention.



FIG. 4 is a block diagram of a contaminant removal device in accordance with another embodiment of the invention.



FIG. 5 is a block diagram of a contaminant removal device in accordance with another embodiment of the invention.



FIG. 6 is a block diagram of a system for producing a refined oil product in accordance with an embodiment of the invention.



FIG. 7 is a graph of free fatty acid concentrations in samples after processing with varying amounts of metal oxide media.



FIG. 8 is a graph of free fatty acid concentrations in samples after processing with varying amounts of metal oxide media.



FIG. 9 is a graph of free fatty acid concentrations in samples after processing with varying amounts of metal oxide media.



FIG. 10 is a graph of free fatty acid concentrations in samples after processing with varying amounts of metal oxide media.



FIG. 11 is a graph of free fatty acid concentrations in samples after processing with varying amounts of metal oxide media.



FIG. 12 is a graph of free fatty acid concentrations in samples after processing with varying amounts of metal oxide media.



FIG. 13 is a schematic diagram of an exemplary process and system in accordance with an embodiment of the invention.



FIG. 14 is a schematic diagram of another exemplary process and system in accordance with an embodiment of the invention.



FIG. 15 is a schematic diagram of another exemplary process and system in accordance with an embodiment of the invention.





While the invention is susceptible to various modifications and alternative forms, specifics thereof have been shown by way of example and drawings, and will be described in detail. It should be understood, however, that the invention is not limited to the particular embodiments described. On the contrary, the intention is to cover modifications, equivalents, and alternatives falling within the spirit and scope of the invention.


DETAILED DESCRIPTION OF THE INVENTION

The embodiments of the present invention described herein are not intended to be exhaustive or to limit the invention to the precise forms disclosed in the following detailed description. Rather, the embodiments are chosen and described so that others skilled in the art can appreciate and understand the principles and practices of the present invention.


All publications and patents mentioned herein are hereby incorporated by reference. The publications and patents disclosed herein are provided solely for their disclosure. Nothing herein is to be construed as an admission that the inventors are not entitled to antedate any publication and/or patent, including any publication and/or patent cited herein.


As described above, the removal of contaminants, such as organic acids (including fatty acids), from chemical compositions is an important commercial process. As shown herein, metal oxide media containing acid/base surface properties such as Lewis acid sites, Bronsted base sites, and/or Bronsted acid sites can be used to selectively bind contaminants from mixed chemical compositions. After the contaminants are bound to the metal oxide, the purified chemical composition can be separated out, leaving behind the metal oxide media and bound contaminants, such as organic acids. In an embodiment, the invention includes a method for removing contaminants from a crude product mixture. The method can include the operation of contacting the crude product mixture with a metal oxide substrate, the metal oxide substrate having acid/base characteristics sufficient to bond with contaminants in the crude product mixture, thereby removing free organic acids and forming a refined product mixture. The method can also include the operation of separating the refined product mixture from the metal oxide media.


Metal oxides media used with embodiments of the invention can include metal oxides with surfaces including Lewis acid sites, Bronsted base sites, and Bronsted acid sites. By definition, a Lewis acid is an electron pair acceptor. A Bronsted base is a proton acceptor and a Bronsted acid is a proton donor. Metal oxides of the invention can specifically include zirconia, alumina, titania and hafnia. Metal oxides of the invention can specifically include oxides of Group IV metals. Metal oxides of the invention can also include silica clad with a metal oxide selected from the group consisting of zirconia, alumina, titania, hafnia, zinc oxide, copper oxide, magnesium oxide and iron oxide. In some embodiments, metal oxides of the invention can include mixtures of metal oxides, such as mixtures of zirconia, alumina, titania and/or hafnia. In other embodiments, the metal oxides used can be substantially pure metal oxides, such as substantially pure zirconia, alumina, titania and/or hafnia. Of the various metal oxides that can be used with embodiments of the invention, zirconia, titania and hafnia are advantageous as they are very chemically and thermally stable and can withstand very high temperatures and pressures as well as extremes in pH.


Metal oxides of the invention can include metal oxide particles clad with carbon. Carbon clad metal oxide particles can be made using various techniques such as the procedures described in U.S. Pat. Nos. 5,108,597; 5,254,262; 5,346,619; 5,271,833; and 5,182,016, the contents of which are herein incorporated by reference. Carbon cladding on metal oxide particles can render the surface of the particles more hydrophobic.


Metal oxide media of the invention can be made in various ways. As one example, a colloidal dispersion of zirconium dioxide can be spray dried to produce aggregated zirconium dioxide particles. Colloidal dispersions of zirconium dioxide are commercially available from Nyacol Nano Technologies, Inc., Ashland, Mass. The average diameter of particles produced using a spray drying technique can be varied by changing the spray drying conditions. Examples of spray drying techniques are described in U.S. Pat. Nos. 4,138,336 and 5,108,597, the content of both of which are herein incorporated by reference. It will be appreciated that other methods can also be used to create metal oxide particles. One example is an oil emulsion technique as described in Robichaud et al., Technical Note, “An Improved Oil Emulsion Synthesis Method for Large, Porous Zirconia Particles for Packed- or Fluidized-Bed Protein Chromatography,” Sep. Sci. Technol. 32, 2547-59 (1997). A second example is the formation of metal oxide particles by polymer induced colloidal aggregation as described in M. J. Annen, R. Kizhappali, P. W. Carr, and A. McCormick, “Development of Porous Zirconia Spheres by Polymerization-Induced Colloid Aggregation-Effect of Polymerization Rate,” J. Mater. Sci. 29, 6123-30 (1994). A polymer induced colloidal aggregation technique is also described in U.S. Pat. No. 5,540,834, the content of which is herein incorporated by reference.


Metal oxide media used in embodiments of the invention can be sintered by heating them in a furnace or other heating device at a relatively high temperature. In some embodiments, the metal oxide is sintered at a temperature of 160° C. or greater. In some embodiments, the metal oxide is sintered at a temperature of 400° C. or greater. In some embodiments, the metal oxide is sintered at a temperature of 600° C. or greater. Sintering can be done for various amounts of time depending on the desired effect. Sintering can make metal oxide media more durable. In some embodiments, the metal oxide is sintered for more than about 30 minutes. In some embodiments, the metal oxide is sintered for more than about 3 hours. However, sintering also reduces the surface area. In some embodiments, the metal oxide is sintered for less than about 1 week.


In some embodiments, the metal oxide media is in the form of particles. Particles within a desired size range can be specifically selected for use in embodiments herein. For example, particles can be sorted by size such as by air classification, elutriation, settling fractionation, or mechanical screening. In some embodiments, the size of the particles is greater than about 0.2 μm. In some embodiments, the size range selected is from about 0.2 μm to about 2 mm. In some embodiments, the size range selected is from about 1 μm to about 100 μm. In some embodiments, the size range selected is from about 5 μm to about 15 μm. In some embodiments, the size range selected is about 10 μm. In some embodiments, the size range selected is about 5 μm.


It can be desirable to maximize the surface area of the metal oxide media so that the amount of organic acids bound by the media is maximized. As such, in some embodiments, metal oxide media used with embodiments of the invention includes porous particles. By way of example, in some embodiments the metal oxide particles can have an average pore size of about 30 angstroms to about 2000 angstroms. However, in other embodiments, the metal oxide particles used are non-porous.


The Lewis acid sites on metal oxides of the invention can interact with Lewis basic compounds. Thus, Lewis basic compounds can be bonded to the surface of metal oxides of the invention. A Lewis base is an electron pair donor. Lewis basic compounds of the invention can include anions formed from the dissociation of acids such as hydrobromic acid, hydrochloric acid, hydroiodic acid, nitric acid, sulfuric acid, perchloric acid, boric acid, chloric acid, phosphoric acid, pyrophosphoric acid, methanethiol, chromic acid, permanganic acid, phytic acid and ethylenediamine tetramethyl phosphonic acid (EDTPA). Lewis basic compounds of the invention can also include hydroxide ion as formed from the dissociation of bases such as sodium hydroxide, potassium hydroxide, lithium hydroxide and the like.


The anion of an acid can be bonded to a metal oxide of the invention by refluxing the metal oxide in an acid solution. By way of example, metal oxide particles can be refluxed in a solution of sulfuric acid. Alternatively, the anion formed from dissociation of a base, such as the hydroxide ion formed from dissociation of sodium hydroxide, can be bonded to a metal oxide by refluxing in a base solution. By way of example, metal oxide particles can be refluxed in a solution of sodium hydroxide. The base or acid modification can be achieved under exposure to the acid or base in either batch or continuous flow conditions when disposed in a reactor housing at elevated temperature and pressure to speed up the adsorption/modification process. In some embodiments, fluoride ion, such as formed by the dissociation of sodium fluoride, can be bonded to the particles.


While not intending to be bound by theory, it is believed that the ability of metal oxides to remove contaminants is related to Lewis acid sites on the metal oxide binding with contaminants that have Lewis basic characteristics. As such, in some embodiments contaminants removed by systems herein include compounds with Lewis basic characteristics. While not limiting the scope herein, exemplary contaminants can include carboxylic acids, phosphates, sulfates, phenols, and the like. By way of further example, the contaminants can include those compounds with stronger Lewis base characteristics than the desired compounds in the composition that is being purified. Biodiesel fuel typically includes esters as desired compounds. As such, in some embodiments contaminants removed from a fuel composition can include all compounds having stronger Lewis base characteristics than the esters in the fuel composition. Organic acids removed with methods and devices of the invention can specifically include carboxylic acids. Organic acids removed with methods and devices of the invention can specifically include free fatty acids.


In some embodiments, at least some water is included in the composition to be purified because organic acids become strong Lewis bases when they are able to ionize, which is facilitated by the presence of water. In some embodiments, the water is already present in the composition to be purified. In other embodiments, some water may be added to the composition to be purified. In still other embodiments, sufficient water may already be present on the metal oxide.


In some embodiments, metal oxide particles can be packed into a housing, such as a column or bed. Disposing metal oxide particles in a housing is one approach to facilitating continuous flow processes. Many different techniques may be used for packing the metal oxide particles into a housing. The specific technique used may depend on factors such as the average particle size, the type of housing used, etc. Generally speaking, particles with an average size of about 1-20 microns can be packed under pressure and particles with an average size larger than 20 microns can be packed by dry-packing/tapping methods or by low pressure slurry packing. In some embodiments, the metal oxide particles of the invention can be impregnated into a membrane, such as a PTFE membrane.


In some embodiments, metal oxide media used with embodiments of the invention is not in particulate form. For example, a layer of a metal oxide can be disposed on a substrate in order to form media used with embodiments of the invention. The substrate can be a surface that is configured to contact the unrefined chemical composition during processing. In one approach, metal oxide media can be disposed as a layer over a surface of a housing that contacts the unrefined chemical composition. Alternatively, the metal oxide media can be embedded as a particulate in the surface of an element that is configured to contact the unrefined chemical composition during processing.


In various embodiments, the metal oxide media can be regenerated after it has reached saturation. For example, in some embodiments, the metal oxide media can withstand high temperatures and the bound organic acids can be burned off. Specifically, the metal oxide media can be exposed to high temperatures in the presence of oxygen and bound organic acids can be combusted.


In other embodiments, the metal oxide media can be flushed with a supercritical alcohol, such as supercritical methanol, simultaneously removing bound fatty acids and esterifying them to form fatty acid methyl esters, a relatively high value by-product. Some examples of reactor systems including such elements will now be described in greater detail.


Referring now to FIG. 1, an embodiment of an organic acid removal device 100 is shown in accordance with an embodiment of the invention. The organic acid removal device 100 includes a housing 104 defining an interior volume. Metal oxide media can be disposed within the interior volume of the housing 104. In some embodiments, metal oxide media can be tightly packed within the interior volume of the housing 104. A crude product mixture (such as a crude vegetable oil or fatty acid methyl ester composition) containing free organic acids can be pumped into the housing 104 through a first conduit 102. After contacting the metal oxide media, free fatty acids in the crude product mixture become bound to the metal oxide media. The now refined product mixture then passes out of the housing 104 through a second conduit 106.


As free organic acids are bound to the metal oxide media, the media can become saturated. As such, some embodiments of the invention include components and methods for regeneration of the metal oxide media. Referring now to FIG. 2, a block diagram of a free organic acid removal device 200 is shown in accordance with another embodiment of the invention. A crude product mixture is pumped from a crude product reservoir 208. The crude product mixture passes through a control valve 210 before passing into a housing 204 that holds metal oxide media. After contacting the metal oxide media, free organic acids in the crude product mixture become bound to the metal oxide media. The now refined product mixture then passes out of the housing 204 though a second control valve 212 and into a refined product reservoir 214.


When the metal oxide media becomes saturated, control valve 210 can be actuated to take the crude product reservoir 208 off-line and put a gas supply source 206 on-line. A gas, including at least a portion of oxygen, can be pumped from the gas supply source 206, through the control valve 210 and into the housing 204. Simultaneously, the housing 204 can be heated with a heating element 218. The combination of the gas and heat result in combustion of the bound organic acids, thereby returning the metal oxide media to a state where more free organic acids can be bound. Control valve 212 can be actuated so that the effluent gas, including combustion products, can pass through control valve 212 before passing out of the device through a vent 220. After the metal oxide media is regenerated, then both of the control valves 210, 212 can be actuated so that a crude product mixture can once again flow into the housing 204 for removal of free organic acids.


In some embodiments, organic acids, such as fatty acids, bound to the metal oxide media can be processed in order to produce a relatively high value by-product. By way of example, an alcohol can be used to both remove the bound fatty acids from the metal oxide media and also convert the fatty acids, through an esterification reaction, into fatty acid alkyl esters. As a specific example, methanol, under supercritical conditions, can be contacted with the metal oxide media in order to esterify the fatty acids producing fatty acid methyl esters.


Referring now to FIG. 3, a block diagram of an organic acid removal device 300 is shown in accordance with another embodiment of the invention. A crude product mixture is pumped from a crude product reservoir 308. The crude product mixture passes through a control valve 310 before passing into a housing that holds metal oxide media. After contacting the metal oxide media, free fatty acids in the crude product mixture are bound to the metal oxide media. The now refined product mixture then passes out of the housing 304 though a second control valve 312 and into a refined product reservoir 314.


When the metal oxide media becomes saturated, control valve 310 can be actuated to take the crude product reservoir 308 off-line and put an alcohol supply tank 306 on-line. An alcohol, under subcritical or supercritical conditions, can be pumped from the alcohol supply tank 306, through the control valve 310 and into the housing 304. Simultaneously, the housing 304 can be heated with a heating element 318, to aid in maintaining the supercritical conditions of the alcohol inside the housing 304. The alcohol esterifies the bound fatty acids and/or displaces the bound free fatty acid and removes them from the metal oxide media, thereby returning the metal oxide media to a state where more free fatty acids can be bound. Control valve 312 can be actuated so that the effluent fatty acid alkyl esters can pass through control valve 312 before being collected in a tank 316. In some embodiments, residual methanol in the effluent fatty acid alkyl ester composition can be removed through a distillation process, or a similar separation process, and then recycled. After the metal oxide media is regenerated, then both of the control valves 310, 312 can be actuated so that a crude product mixture can once again flow into the housing 304 for removal of free fatty acids.


In can be advantageous to remove organic acids from crude product mixtures in a continuous or semi-continuous process. In some embodiments, the invention can include device and methods for both removing free fatty acids and regenerating the metal oxide media as part of a semi-continuous process. Referring now to FIG. 4, a block diagram of an organic acid removal device 400 is shown in accordance with another embodiment of the invention. In this embodiment, both a first housing 404 containing metal oxide media and a second housing 418 including metal oxide media are included. Control valves 410, 412, 420, and 422, can be actuated such that the crude product mixture is routed through one housing for organic acid removal while metal oxide media in the other housing is being regenerated.


For example, a crude product mixture is pumped from a crude product reservoir 408 and passes through a control valve 420 before passing into a first housing 404 that holds metal oxide media. After contacting the metal oxide media, free organic acids in the crude product mixture become bound to the metal oxide media. The now refined product mixture then passes out of the housing 404 though a second control valve 422 and into a refined product reservoir 414. Simultaneously, methanol or another displacing or reactive liquid, or a gas including oxygen, can be pumped from a storage reservoir 406 through a third control valve 410 and into a second housing 418 that hold metal oxide media. The bound organic acids can be removed from the metal oxide media, and thus the metal oxide media can be regenerated by the displacing liquid or gas. In embodiments where methanol is used and the organic acid includes fatty acids, the resulting fatty acid methyl esters can be pumped through a fourth control valve 412, and into a storage tank 416, or passed along for further processing.


After the metal oxide media in the first housing 404 becomes saturated with organic acids, the processes can be reversed. Specifically, valves 410, 412, 420, and 422 can be actuated in order to cause the crude product mixture to pass into housing 418 instead of housing 404. The refined product mixture can then pass from housing 418 to refined product reservoir 414. In addition, the methanol or oxygen containing gas can be passed through housing 404 instead of housing 418. In the case of methanol and fatty acids, the resulting fatty acid alkyl esters can be passed into storage tank 416.


Various techniques can be used to determine when the metal oxide media is saturated and, therefore, when it is time to regenerate the same. In some embodiments, this can be accomplished though a calculation of the binding capacity of the metal oxide media used and the concentration of organic acids in the crude product mixture. Hypothetically, if it is known that a gram of the metal oxide can bind the amount of organic acids contained in one liter of a particular crude product mixture, then, at maximum, a liter of the crude product mixture can be run through an organic acid removal device for every gram of metal oxide media in the device, before the metal oxide media is saturated.


In some embodiments, a sensor can be used in order to determine the concentration of organic acids in the refined composition after contacting the metal oxide media. If the concentration of organic acids is observed to rise, then this can be taken as an indication that the metal oxide media being used has become saturated. Various types of sensors can be used to detect or estimate concentrations of organic acids. By way of example, various chromatographic techniques can be used to assess organic acid concentrations. In another embodiment, a pH sensor can be used. In general, a refined product mixture will exhibit a pH that is more alkaline than an otherwise identical product mixture having a greater concentration of organic acids. As such, changes in the pH of the product mixture coming out of the housing containing the metal oxide media can be used to indicate when the metal oxide media has become saturated. An exemplary pH sensor is described in U.S. Pat. No. 4,582,589, the content of which is herein incorporated by reference. However, it will be appreciated that many other types of pH sensors and analyzers (HPLC, GC, IR, NMR, MS) can be used. The analyzer can either be installed online or employed offline for FFA determination of the system effluent.


Referring now to FIG. 5, a block diagram of an organic acid removal device 500 is shown in accordance with another embodiment of the invention. A crude product mixture is pumped from a crude product reservoir 508. The crude product mixture passes through a control valve 510 before passing into a housing 504 that holds metal oxide media. After contacting the metal oxide media, free fatty acids in the crude product mixture become bound to the metal oxide media. The now refined product mixture then passes out of the housing 504 and though a sensor unit 518. The sensor unit 518 can be used to evaluate when the metal oxide media needs to be regenerated. For example, the sensor unit 518 can include a pH sensor and can monitor the pH of the refined product mixture passing out of the housing 504. The refined product mixture can then pass through second control valve 512 and into a refined product reservoir 514.


When the metal oxide media becomes saturated, as indicated by the sensor unit 518, the control valve 510 can be actuated to take the crude product reservoir 508 off-line and put an alcohol supply tank 506 on-line. An alcohol, under supercritical conditions, can be pumped from the alcohol supply tank 506, through the control valve 510 and into the housing 504, esterifying the bound fatty acids and removing them from the metal oxide media, thereby returning the metal oxide media to a state where more free fatty acids can be bound. Control valve 512 can be actuated so that the effluent fatty acid alkyl esters can pass through control valve 512 before being collected in a tank 516. After the metal oxide media is regenerated, then both of the control valves 510, 512 can be actuated so that a crude product mixture can once again flow into the housing 504 for removal of free fatty acids.


It will be appreciated that the percentage of organic acids removed by the metal oxide media will depend on various factors including the residence time of the crude product mixture within the housing, the temperature of the crude product mixture, and the binding capacity of the metal oxide media. However, it will be appreciated that by adjusting parameters associated with the process, the amount of free organic acids removed from the crude product mixture can be controlled. In some embodiments, at least about 50% of the free organic acids in a crude product mixture are removed after refining the same with a free organic acid removal device as described herein. In some embodiments, at least about 90% of the free organic acids in a crude product mixture are removed after refining the same with a free organic acid removal device as described herein. In some embodiments, at least about 99% of the free organic acids in a crude product mixture are removed after refining the same with a free organic acid removal device as described herein.


In some embodiments, the reaction mixture reaches the desired level of completion after one pass over a metal oxide media bed or packing. However, in other embodiments, the effluent flow may be rerouted over the same metal oxide media or routed over another metal oxide media bed or packing so that a larger percentage of free organic acids are removed.


In some embodiments, two different metal oxides (such as zirconia and titania) can be separately formed but then disposed together within a single housing. In such an approach, the crude product mixture passing over metal oxide media can be simultaneously exposed to both metal oxides.


In some embodiments, devices for removal of contaminants as described herein can be used in conjunction with equipment for producing oil products. For example in some embodiments, devices or system for removal of contaminants as included herein can be coupled with a biodiesel production plant. Exemplary methods and system of producing biodiesel fuel that can be used as part of various embodiments herein are described in U.S. patent application Ser. No. 11/833,839, (U.S. Pat. No. 7,897,798) the content of which is herein incorporated by reference in its entirety.


In some embodiments, devices or systems for removal of contaminants can be used in conjunction with equipment such as mechanical presses, solvent extraction tanks, evaporators, and the like. For example, in a process for producing a refined oil product from a raw material various preparative steps can occur first including cleaning, drying and, in the case of a plant produce with hulls, dehulling. After the raw material is prepared, it can optionally be heated in order to coagulate proteins to make the oil extraction process easier.


In the solvent extraction process, the raw material can be cut into flakes which are put in percolation extractors and immersed in a solvent, such as hexane. The crude oil is solvated by the solvent and then separated from the flakes. The solvent is then separated from the crude oil, such as with an evaporator. The crude oil can then be passed through a device for the removal of organic acids as described herein.


In the mechanical pressing process, the raw material is typically crushed and then pressed in a mechanical press to yield a crude oil. The crude oil can then be passed through a device for the removal of organic acids as described herein.


In some embodiments, other purification steps can also be taken including degumming (removing of phosphatides) and bleaching (with activated earth or activated carbon to remove color and other impurities).


Referring now to FIG. 6, a system for producing a refined oil product in accordance with an embodiment of the invention is schematically illustrated. The system 600 includes a preprocessing module 602 configured to prepare a raw material for oil extraction. The preprocessing module 602 can include washing stations, drying ovens, dehulling mills, chopping stations, crushing devices, flaking devices, and the like. Then the raw material can pass on to an oil extraction module 604. In some embodiments, the oil extraction module 604 can include a mechanical press. In other embodiments, the oil extraction module 604 can include a percolation extractor and a solvent evaporator. Then the resulting crude oil can be passed through a device 606 for the removal of organic acids as described herein. In an embodiment, the device 606 can include a housing defining an interior volume with metal oxide media disposed therein. Then, in some embodiments, the refined oil product can pass through a sensor module 608 configured to determine the amount of organic acids remaining in the refined oil product. In some embodiments, the refined oil product can be passed along for further processing. In other embodiments, the refined oil product can be collected in a refined oil storage tank 610.


Crude Product Mixtures (Feed Stocks)


Devices and methods of the invention can be used as part of the process of producing and/or refining various types of organic acid containing plant, animal, and microbe feed stocks. By way of example, devices and methods of the invention can be used in the process of producing and/or refining rapeseed oil, soybean oil, canola oil, cottonseed oil, grape seed oil, mustard seed oil, corn oil, linseed oil, safflower oil, sunflower oil, poppy-seed oil, pecan oil, walnut oil, oat oil, peanut oil, rice bran oil, camellia oil, castor oil, olive oil, palm oil, coconut oil, rice oil, algae oil, seaweed oil, and Chinese Tallow tree oil. Crude product mixtures processed with embodiments of the invention can also include components of argan, avocado, babassu palm, balanites, borneo tallow nut, brazil nut, calendula, camelina, caryocar, cashew nut, chinese vegetable tallow, cocoa, coffee, cohune palm, coriander, cucurbitaceae, euphorbia, hemp, illipe, jatropha, jojoba, kenaf, kusum, macadamia nuts, mango seed, noog abyssinia, nutmeg, opium poppy, perilla, pili nut, pumpkin seed, rice bran, sacha inche, seje, sesame, shea nut, switch grass, teased, allanblackia, almond, chaulmoogra, cuphea, jatropa curgas, karanja seed, neem, papaya, tonka bean, tung, ucuuba, cajuput, clausena anisata, davana, galbanum natural oleoresin, german chamomile, hexastylis, high-geraniol monarda, juniapa-hinojo sabalero, lupine, melissa officinalis, milfoil, ninde, patchouli, tarragon, and wormwood.


Many different crude product mixtures derived from animals can be processed with embodiments of the invention. By way of example, animal-based crude product mixtures can include choice white grease, lard (pork fat), tallow (beef fat), fish oil, and poultry fat. Many different crude product mixtures derived from microorganisms (Eukaryotes, Bacteria and Archaea) can be processed with embodiments of the invention. By way of example, microbe-based crude product mixtures can include the L-glycerol lipids of Archaea and algae and diatom oils.


In some embodiments, crude product mixtures used herein can be derived from both plant and animal sources such as yellow grease, white grease, and brown grease, soapstock and acidulated soapstock. By way of example, yellow, white or brown grease can include frying oils from deep fryers and can thus include fats of both plant and animal origin. Crude product mixtures can specifically include used cooking oil. Brown grease (also known as trap grease) can include fats extracted from sewage systems and can thus include fats of both plant and animal origin.


It will be appreciated that devices and methods herein can also be used to process and/or refine (or “polish”) fuel compositions, such as fatty acid methyl ester compositions. For example, in some embodiments, devices and methods herein can be used to polish biodiesel compositions.


The present invention may be better understood with reference to the following examples. These examples are intended to be representative of specific embodiments of the invention, and are not intended as limiting the scope of the invention.


EXAMPLES
Example 1
Formation of Zirconia Particles

A colloidal dispersion of zirconium oxide (NYACOL™ ZR 100/20) (Nyacol Nano Technologies, Inc., Ashland, Mass.), containing 20 wt. % ZrO2 primarily at about 100 nm particles was spray dried. As the dispersion dried, the particles interacted strongly with one another to provide aggregated ZrO2 particles. The dried aggregated particles that were obtained were examined under an optical microscope and observed to consist mostly of spherules from about 0.5 μm to about 15 μm in diameter.


The dried spherules were then sintered by heating them in a furnace at a temperature of 750° C. for 6 hours. The spherules were air classified, and the fraction having a size of approximately 10 μm was subsequently isolated. The particles were all washed in sodium hydroxide (1.0 M), followed by water, nitric acid (1.0 M), water and then dried under vacuum at 110° C. BET nitrogen porosimetry was performed in order to further characterize the sintered spherules. The physical characteristics of the spherules were as listed below in Table 2.












TABLE 2









Surface area (m{circumflex over ( )}2/g)
22.1



Pore volume (mL/g)
0.13



Pore diameter (angstrom)
240



Internal Porosity
0.44



Average size (micron)
10.23



Size Standard Deviation (μm)
2.62



D90/D10 (Size Distribution)
1.82










Example 2
Formation of Base/Acid Modified Zirconia Particles

1000 g of zirconia particles, prepared according to Example 1, were put into a polyethylene bottle. 1.5 liters of deionized water was put into it and shaken strongly. Half of the suspension was put into a 4000 ml glass Erlenmeyer flask, 2000 ml of deionized water was added into it and the mixture was sonicated under vacuum for 30 minutes to get the water into the pores of the particles. The suspension was then put into 20 L bucket. The same procedure was repeated on the other half of the suspension. The particles were transferred to a plastic container. The particles were rinsed with a carbonate free 0.5 M NaOH solution. Then the suspension was stirred for 8 hours.


The NaOH solution was then decanted and then the particles were rinsed twice with carbonate free purified water (2 L in total). The water was then removed. 0.5 M HNO3 was added to the particles at a ratio of 10:1 (v/m). The suspension was then shaken for 8 hours.


The nitric acid solution was then removed. The particles were then rinsed three times with deionized water 3-4 times until reaching a pH=5-6. The particles were filtered and then rinsed with ethanol. The particles were placed in a clean container and dried under vacuum at 120° C. for 5 hours.


Example 3
Adsorption of Fatty Acids in Biodiesel Using Base/Acid Modified Zirconia

10 g, 5 g, 2.5 g, and 1.0 g samples of base/acid modified zirconia (zirconium dioxide) particles as formed in Example 2 were added to 50 mL centrifuge tubes, respectively. 10 g of a biodiesel composition, known to contain 4% fatty acids, were put into each tube. The tubes were shaken to suspend the particles, sonicated for 10 minutes, and then put under vacuum for 5 minutes each. The samples were held at room temperature for 10 minutes. Finally, the samples were centrifuged at 3750 rpm for 5 minutes. An acid titration was then performed on 5 g of each treated sample according to ASTM Method D664-04.


The above experimental procedure was then duplicated. The results of both trials are shown in FIG. 7. As FIG. 7 shows, the reproducibility between the two trials was very good. The average binding capacity of fatty acids on zirconia was 12.6 mg/g, which is equivalent to 1.76 micromol/m2.


Example 4
Formation of Base Modified Zirconia Particles

1 liter of 2.0 M sodium hydroxide was placed in a 2 liter plastic Erlenmeyer flask. 110 g of 5-15 diameter μm bare zirconia, prepared as described in Example 1, was put into the flask. The particle suspension was sonicated for 10 minutes under vacuum and then swirled for 2 hours at ambient temperature. The particles were then allowed to settle and the base solution was decanted. Then, 1.4 liters of HPLC-grade water was added to the flask followed by settling decanting. Then, 200 mL of HPLC-grade water was added back to the flask and the particles were collected on a nylon filter with 0.45 micron pores. The collected particles were then washed with 2 aliquots of 200 mL HPLC-grade water followed by 3 aliquots of 200 mL of HPLC-grade methanol. Air was then passed through the particles until they were free-flowing.


Example 5
Adsorption of Fatty Acids in Biodiesel Using Base Modified Zirconia

10 g of base modified zirconia (zirconium dioxide) particles as formed in Example 4 was added to 50 mL centrifuge tube. 10 g of a biodiesel composition, known to contain 4% fatty acids, was put into the tube. The tube was shaken to suspend the particles, sonicated for 10 minutes, and then put under vacuum for 5 minutes. The sample was held at room temperature for 10 minutes. Finally, the sample was centrifuged at 3750 rpm for 5 minutes. An acid titration was then performed on 5 g of the sample according to ASTM Method D664-04.


The results show that the average binding capacity of fatty acids on zirconia is 13.2 mg/g, which is close to results obtained on base modified zirconia.


Example 6
Adsorption of Fatty Acids in Biodiesel Using Unmodified Titania

10 g, 5 g, 2.5 g, and 1.0 g samples of unmodified titania particles (20 μm diameter/100 Å average pore size, ZirChrom Separations, Inc, Anoka, Minn.) were added to 50 mL centrifuge tubes, respectively. 10 g of a biodiesel composition, known to contain 4% fatty acids, were put into each tube. The tubes were shaken to suspend the particles, sonicated for 10 minutes, and then put under vacuum for 5 minutes each. The samples were held at room temperature for 10 minutes. Finally, the samples were centrifuged at 3750 rpm for 5 minutes. An acid titration was then performed on 5 g of each treated sample based on ASTM methods. The adsorption results are shown in FIG. 8. The average binding capacity of fatty acids on unmodified titania was calculated to be 11.7 mg/g.


Example 7
Heat Treatment of Fatty Acid Saturated Zirconia Particles

The fatty acid saturated zirconia particles from Example 3 were collected by filtration with a 0.45 μm membrane. The particles were washed with 3×150 mL hexane to remove the residual biodiesel composition. The particles were then dried under vacuum.


The dried particles were then heated to 845° F. in the presence of oxygen for four hours to combust the fatty acids on the zirconia surface. Then the regenerated particles were cooled down to room temperature.


Example 8
Adsorption of Fatty Acids in Biodiesel by Using Regenerated Zirconia Particles

10 g, 5 g, 2.5 g, and 1.0 g samples of regenerated zirconia particles as formed in Example 7 were added to 50 mL centrifuge tubes, respectively. 10 g of a biodiesel composition, known to contain 4.1% fatty acids, were put into each tube. The tubes were shaken to suspend the particles, sonicated for 10 minutes, and then put under vacuum for 5 minutes each. The samples were held at room temperature for 10 minutes. Finally, the samples were centrifuged at 3750 rpm for 5 minutes. An acid titration was then performed on 5 g of each treated sample according to ASTM method D664-04. The adsorption results are shown in FIG. 9. The average binding capacity of fatty acids on regenerated zirconia was calculated to be 13.2 mg/g, which is very close to the binding capacity value (12.6 mg/g) obtained in example 3. The data suggest that saturated metal oxide particles can be completely regenerated by heat-treatment.


Example 9
Adsorption of Fatty Acids in Biodiesel Using Basic Alumina

10 g, 5 g, 2.5 g, and 1.0 g samples of unmodified basic alumina particles (150 mesh diameter/58 Å average pore size, surface area 155 m2/g, pH 9.5±0.5 in H2O, Sigma-Aldrich, St. Louis, Mo.) were added to 50 mL centrifuge tubes, respectively. 10 g of a biodiesel composition, known to contain 4.2% fatty acids, was put into each centrifuge tube. The tubes were shaken to suspend the particles, sonicated for 10 minutes, and then put under vacuum for 5 minutes each. The samples were held at room temperature for 10 minutes. Finally, the samples were centrifuged at 3750 rpm for 5 minutes. An acid titration was then performed on 5 g of each treated sample based on ASTM methods (ASTM METHOD D664-04). The adsorption results are shown in FIG. 10. The average static binding capacity of fatty acids on basic alumina was calculated to be about 158.9 mg/g.


Example 10
Adsorption of Fatty Acids in Biodiesel Using Neutral Alumina

10 g, 5 g, 2.5 g, and 1.0 g samples of unmodified neutral alumina particles (150 mesh diameter/58 Å average pore size, 155 m2/g surface area, pH 7.0±0.5 in H2O, Sigma-Aldrich, St. Louis, Mo.) were added to 50 mL centrifuge tubes, respectively. 10 g of a biodiesel composition, known to contain 4.2% fatty acids, were put into each tube. The tubes were shaken to suspend the particles, sonicated for 10 minutes, and then put under vacuum for 5 minutes each. The samples were held at room temperature for 10 minutes. Finally, the samples were centrifuged at 3750 rpm for 5 minutes. An acid titration was then performed on 5 g of each treated sample based on ASTM methods (ASTM METHOD D664-04). The adsorption results are shown in FIG. 11. The average static binding capacity of fatty acids on neutral alumina was calculated to be about 149.2 mg/g.


Example 11
Adsorption of Fatty Acids in Biodiesel Using Acidic Aluminia

10 g, 5 g, 2.5 g, and 1.0 g samples of unmodified acidic alumina particles (150 mesh diameter/58 Å average pore size, 155 m2/g surface area, pH 4.5±0.5 in H2O, Sigma-Aldrich, St. Louis, Mo.) were added to 50 mL centrifuge tubes, respectively. 10 g of a biodiesel composition, known to contain 4.2% fatty acids, were put into each tube. The tubes were shaken to suspend the particles, sonicated for 10 minutes, and then put under vacuum for 5 minutes each. The samples were held at room temperature for 10 minutes. Finally, the samples were centrifuged at 3,750 rpm for 5 minutes. An acid titration was then performed on 5 g of each treated sample based on ASTM methods (ASTM METHOD D664-04). The adsorption results are shown in FIG. 12. The average static binding capacity of fatty acids on acidic alumina was calculated to be about 107.1 mg/g.


Example 12
Continuous Removal of Fatty Acids in Biodiesel Using Unmodified Titania

(A) Loading Step


A system was set up for the removal of fatty acids as shown in FIG. 13. The system included a high-pressure pump 1306 that drew from a biodiesel reservoir 1302 at 5 ml/min or 10 ml/min. The biodiesel reservoir was continuously sparged with nitrogen to remove dissolved oxygen from the biodiesel feedstock. The biodiesel was pumped through a preheater 1310 before entering a fixed bed reactor 1312 (50 cm length with 21.2 mm i.d.) packed with 234.33 g of unmodified titania (80 μm diameter/60 Å average pore size, ZirChrom Separations, Inc, Anoka, Minn.) to adsorb the fatty acids in the biodiesel. However, the loading step was performed at ambient temperature (≈20 degrees Celsius). After the reactor, the biodiesel passed through a heat exchanger 1314 and a back pressure regulator 1316. The treated biodiesel was then collected in a 100 mL plastic bottle at every 10 minutes. The collected samples were distilled at 75° C. under 500 mbar pressure to remove residual methanol. An acid titration was then performed on 5 g of each distilled sample based on ASTM methods (ASTM METHOD D664-04) to obtain an acid number.


(B) Washing Step


Methanol was used to displace the adsorbed fatty acids from the titania and regenerate the system. The system included a second high-pressure pump 1308 that drew from a methanol reservoir 1304 that was continuously sparged with nitrogen to remove dissolved oxygen from the methanol feedstock. The flow rates were 5 ml/min or 10 ml/min. The methanol passed through a preheater 1310 before entering the reactor 1312. After the reactor, it passed through a heat exchanger 1314. After the heat exchanger 1314, the methanol with washed fatty acids from the reactor passed through the backpressure regulator 1316 which prevented methanol from boiling in the reactor 1312. The “cooled” liquid (methanol plus fatty acids) was collected in a flask. The collected sample was distilled at 75° C. under 500 mbar pressure to remove methanol. An acid titration was then performed on 5 g of each distilled sample based on ASTM methods to obtain an acid number. All biodiesel samples met ASTM acid number specifications for biodiesel fuel after removal of free fatty acids by the system.


Table 3 shows the conditions used for the experiments and the results obtained. Eight separate trials were run on the same titania. Loading capacities (milligrams of free fatty acids (FFA's) per gram of titania) for each trial was nearly constant indicating that the system may be used for repeated removal of free fatty acids from biodiesel fuel. The recoveries of the biodiesel ranged from 99.3% to 100.1%. This example shows that a metal oxide material can be used to remove free fatty acids from a biodiesel composition with excellent reproducibility and almost complete recovery.











TABLE 3









Trial #
















1
2
3
4
5
6
7
8



















Reactor Diameter
21.2
21.2
21.2
21.2
21.2
21.2
21.2
21.2


(mm)


Reactor Length (mm)
500
500
500
500
500
500
500
500


Preheater Setting
303
303
303
303
303
303
303
306


Temp. at Washing


Step (Celsius)


Actual Temperature
302
301
301
301
302
302
302
302


at Inlet of Reactor


(Celsius)


Actual Temperature
112
113
105
110
119
114
118
176


at Outlet of Reactor


(Celsius)


Flow Rate (ml/min)
5
5
5
5
5
5
5
10


Backpressure (PSI)
2000
2000
2000
2000
2000
2000
2000
2000


Initial Biodiesel
65.2
69.5
64.1
69.05
129.73
147.36
217.81
218.1


Weight (g)


Collected Biodiesel at
61.35
65.3
60.23
65.1
123.13
140.51
209.74
211.42


Loading Step (g)


Collected Biodiesel at
3.4
3.75
3.85
3.65
5.62
5.86
7.35
6.91


Washing Step (g)


Recovery (%)
99.31%
99.35%
99.97%
99.57%
99.24%
99.33%
99.67%
100.11%


Initial FFA (%)
5.35%
5.35%
5.35%
5.35%
5.35%
5.35%
5.35%
5.35%


FFA Weight (g)
3.49
3.72
3.43
3.69
6.94
7.88
11.65
11.67


Capacity of System
25.6
24.8
25
26
24
25
27
29.5


(mg/g)


Acid Number for
0.00
0.00
0.00
0.00
0.06
0.03
0.16
0.18


Treated Samples









Example 13
Continuous Removal of Fatty Acids in Biodiesel Using Basic Alumina

(A) Loading Step


A system was set up for removal of fatty acids as shown in FIG. 13. In this example the high-pressure pump for the biodiesel reservoir was operated at 15 ml/min. The fixed bed reactor (50 cm length with 21.2 mm i.d.) was packed with 234.33 g of basic alumina particles (150 mesh diameter/58 Å average pore size, surface area 155 m2/g, pH 9.5±0.5 in H2O, Sigma-Aldrich, St. Louis, Mo.). The loading step was performed at ambient temperature. The treated biodiesel was collected in a 100 mL plastic bottle at every 10 minutes. The collected samples were distilled at 75° C. under 500 mbar to remove residual methanol. An acid titration was then performed on 5 g of each distilled sample based on ASTM methods (ASTM METHOD D664-04) to obtain an acid number. Results are shown in Table 4 below.


(B) Washing Step


Methanol was used to displace the adsorbed fatty acids from the alumina and regenerate the system. The high-pressure pump for the methanol reservoir was operated at 15 ml/min. The methanol passed through the preheater, reactor, and heat exchanger. After the heat exchanger, the methanol with washed fatty acids from the reactor passed through the backpressure regulator. The “cooled” liquid (methanol plus fatty acids) was collected in a flask. The collected sample was distilled at 75° C. under 500 mbar pressure to remove methanol. An acid titration was then performed on 5 g of each distilled sample based on ASTM methods to obtain an acid number (ASTM METHOD D664-04).


Table 4 shows the conditions used for the experiments and also the reproducibility of the experiments. Four replicate trials were run on the same alumina reactor. All loading capacities were nearly identical. The recovery of the biodiesel from the four trials ranged from 98.62% to 101.1% indicating full recovery within experimental error. The reproducibility of the regeneration of the system was excellent. All biodiesel samples treated by the system were found to meet ASTM acid number requirements for biodiesel fuel with the exception of Trial #1. However, it was determined that the amount of fatty acids used in Trial #1 exceeded the capacity of the system based on the amount of alumina used.











TABLE 4









Trial #












1
2
3
4















Reactor Diameter (mm)
21.2
21.2
21.2
21.2


Reactor Length (mm)
500
500
500
500


Preheater Setting Temp.
303
303
303
303


at Washing Step


(Celsius)


Actual Temperature at
302
301
301
301


Inlet of Reactor (Celsius)


Actual Temperature at
112
113
105
110


Outlet of Reactor


(Celsius)


Flow Rate (ml/min)
15
15
15
15


Backpressure (PSI)
2000
2000
2000
2000


Initial Biodiesel
1002.38
412.61
334.69
338.62


Weight (g)


Collected Biodiesel at
968.01
394.46
317.52
304.68


Loading Step (g)


Collected Biodiesel at
20.53
22.51
17.02
30.54


Washing Step (g)


Recovery (%)
98.62%
101.06%
99.97%
99.57%


Initial FFA (%)
5.35%
5.35%
5.35%
5.35%


FFA Weight (g)
53.63
22.07
17.91
18.12


Capacity of System
107.3
117.7
98.5
124.5


(mg/g)


Acid Number for Treated
3.36
0.14
0.03
0.03


Samples









Example 14
Continuous Removal of Fatty Acids in Biodiesel Production Process

A system for continuously producing biodiesel and removing free fatty acids from the resulting product mixture was set up as shown in FIGS. 14 and 15. FIG. 14 shows the use of two high pressure Waters 590 HPLC pumps 1408 and 1412 obtained from Waters Corporation (Milford, Mass.). One pump 1408 drew from a lipid reservoir 1402. The other pump 1412 drew from an alcohol supply reservoir 1410. Both the lipid reservoir 1402 and the alcohol supply reservoir 1410 were continuously sparged with nitrogen to minimize the effect of dissolved oxygen on the system. The oil feedstock was first filtered by passing the liquid under high pressure through a blank stainless steel 1 cm i.d.×15 cm long filter tube 1406 fitted with two 2 micron stainless steel frits before it entered the heat exchanger 1414 and before it was combined with methanol. Both the alcohol and lipid feedstock streams were pumped into a heat exchanger 1414 that was formed by welding together two ⅛th inch o.d. stainless steel tubes (Alltech Associates, Deerfield, Ill.) with silver solder where the heat from the hot effluent from the reactor is exchanged with the two incoming reactant streams (methanol and lipid). After the heat exchanger 1414 the two reactant streams were combined using a “T” and then passed through an electrically driven preheater 1416 that was capable of bringing the mixture to the desired set point temperature before it enters the independently thermo-stated fixed bed catalytic reactor 1418 (“production reactor”). Temperature control was achieved using EZ-Zone PM Watlow (St. Louis, Mo.) temperature controllers. The preheater 1416 consisted of wound stainless steel HPLC tubing in a grooved aluminum cylindrical block with an 800 watt Watlow heater in the center of the cylinder. The backpressure of the system was maintained through the use of a backpressure regulator 1420 obtained from Tescom (Elk River, Minn.).


A fatty acid removal system, as shown in FIG. 15, was then used to “polish” the biodiesel to meet ASTM specifications. Specifically, the fatty acid removal system included an organic acid removal reactor 1512 (500 mm length by 21.2 mm i.d.) packed with 150 mesh/58 Å aluminum oxide particles (Sigma-Aldrich, St. Louis, Mo.). It was set up vertically with the flow from the bottom to top. The fatty acid removal system was regenerated online by passing nitrogen from a nitrogen supply tank 1506 through the removal reactor 1512 to move the biodiesel and alcohol out, followed by passing air from an air supply tank 1508 through the removal reactor 1512 it to burn/oxidize the residual adsorbed fatty acids and residual biodiesel and methanol. The liquid that was displaced by nitrogen and then air was then cooled and spontaneously separated into two distinct phases; the top phase is primarily comprised of methanol, water and glycerol and the bottom layer is primarily comprised of biodiesel fuel. Phases were separated in a separation weir 1422. The polished biodiesel was distilled 1424 under vacuum (10 mbar) to remove the residual alcohols and volatiles. The residual alcohols were returned to the alcohol supply tank 1410. Any residual glycerol was then separated off leaving polished biodiesel fuel collected in a finished product reservoir 1426.


Table 5 shows the typical conditions of the fatty acid removal system used for polishing the biodiesel and regeneration conditions including heating, and cooling steps.

















TABLE 5






Setting
Inlet
Middle
Outlet
Sampling






Temp.
Temp.
Temp.
Temp.
Time
N2 Flow
Air Flow


Step
(Celsius)
(Celsius)
(Celsius)
(Celsius)
(min.)
(ml/min)
(ml/min)
Notes























Heating
450
25
25
24
0
100

Flushing


Heating
450
78
232
196
5
100

Flushing


Heating
450
150
460
403
10
1500

Flushing


Heating
450
139
473
438
15

1700
Burning


Heating
450
150
473
450
18

1700
Burning


Heating
450
348
469
453
20

1700
Burning


Heating
450
333
463
453
21

1700
Burning


Heating
450
405
459
453
23

1700
Burning


Heating
450
306
452
451
27

1700
Burning


Heating
450
282
453
450
28

1700
Burning


Heating
450
257
528
449
30

1700
Burning


Heating
450
238
521
451
31

1700
Burning


Cooling
OFF
232
510
503
32
100

Flushing


Cooling
OFF
35
50
56
82


Flushing









Acid number of the samples was determined in accordance with ASTM D664-04. Table 6 shows the high reproducibility of fatty acid removal system and its ability to produce biodiesel that meets the ASTM acid number specification (according to ASTM D6751-07a acid number can be no more than 0.5). Some of the samples that passed the ASTM acid number test (acid number no greater than 0.5) were then blended and sent to a third party (FuelOnly, Inc. (ISO9000, Vancouver, Wash.)) for the full battery of ASTM tests applicable to biodiesel under ASTM D6751-07a. This testing revealed that the blended samples passed ASTM specifications for biodiesel fuel.



















TABLE 6

















Passed






Biodiesel


Collection

ASTM



Feed

Biodiesel
Reactor
Acid Number
Biodiesel
Time
Flow
Acid

















Expt. #
Stock
Alcohol
Type
Temp
Before
After
Collected
(min)
Rate
#?




















1
Corn Oil
190 Proof
Ethyl
340
18.00
0.58
93.5
30
3.12
No




Ethanol
esters


2
Corn Oil
190 Proof
Ethyl
340
16.29
0.35
104.45
31
3.37
Yes




Ethanol
esters


3
Corn Oil
190 Proof
Ethyl
340
16.10
0.11
103.94
31
3.35
Yes




Ethanol
esters


4
Corn Oil
190 Proof
Ethyl
340
16.10
0.68
104.83
30.5
3.44
No




Ethanol
esters


5
Corn Oil
190 Proof
Ethyl
340
16.10
0.11
110.94
31.5
3.52
Yes




Ethanol
esters


6
Corn Oil
190 Proof
Ethyl
340
15.87
0.11
105.52
30
3.52
Yes




Ethanol
esters


7
Corn Oil
190 Proof
Ethyl
340
15.87
0.34
103.9
30
3.46
Yes




Ethanol
esters


8
Corn Oil
190 Proof
Ethyl
340
15.87
0.11
104.01
30
3.47
Yes




Ethanol
esters


9
Corn Oil
190 Proof
Ethyl
340
15.94
0
113.97
33
3.45
Yes




Ethanol
esters


10
Corn Oil
190 Proof
Ethyl
340
15.94
0.46
107.54
30.5
3.53
Yes




Ethanol
esters


11
Corn Oil
190 Proof
Ethyl
340
15.94
0
104.46
30
3.48
Yes




Ethanol
esters


12
Corn Oil
190 Proof
Ethyl
340
15.99
0
106.11
30
3.54
Yes




Ethanol
esters


13
Corn Oil
190 Proof
Ethyl
340
15.99
0.56
107.31
30.5
3.52
No




Ethanol
esters


14
Corn Oil
190 Proof
Ethyl
340
19.43
1.81
104.91
21.5
4.88
No




Ethanol
esters


15
Corn Oil
Butanol
Butyl
360
6.04
0
162.19
50.25
3.23
Yes





esters


16
Corn Oil
Butanol
Butyl
360
6.04
0
86.76
27
3.21
Yes





esters


17
Corn Oil
Butanol
Butyl
360
6.04
0.35
35.64
11
3.24
Yes





esters


18
Corn Oil
Butanol
Butyl
360
6.04
0
121.13
36
3.36
Yes





esters


19
Corn Oil
Butanol
Butyl
360
6.04
0.23
47.94
15
3.20
Yes





esters


20
Corn Oil
Butanol
Butyl
360
6.04
0.71
36.8
10
3.68
No





esters


21
Corn Oil
Butanol
Butyl
360
6.04
0.12
160.07
35
4.57
Yes





esters


22
Corn Oil
Butanol
Butyl
360
6.04
0.23
69.51
20
3.48
Yes





esters


23
Corn Oil
Butanol
Butyl
360
6.04
0.35
31.48
10
3.15
Yes





esters


24
Corn Oil
Butanol
Butyl
360
6.04
0.92
31.5
10
3.15
No





esters


25
Corn Oil
Butanol
Butyl
360
6.04
0
163.71
50
3.27
Yes





esters


26
Corn Oil
Butanol
Butyl
360
6.04
0.12
113.95
35
3.26
Yes





esters


27
Corn Oil
Butanol
Butyl
360
6.04
0.93
33.54
10
3.35
No





esters


28
Corn Oil
Butanol
Butyl
360
4.19
0
123.07
35
3.52
Yes





esters


29
Corn Oil
Butanol
Butyl
360
4.19
0
80.3
25
3.21
Yes





esters


30
Corn Oil
Butanol
Butyl
360
4.19
0.12
97.67
25
3.91
Yes





esters


31
Corn Oil
Butanol
Butyl
360
4.19
1.62
65.59
20
3.28
No





esters


32
Corn Oil
Butanol
Butyl
362
9.67
0.12
181.43
35
5.18
Yes





esters


33
Corn Oil
Butanol
Butyl
362
9.67
0.46
168.42
35
4.81
Yes





esters


34
Corn Oil
Butanol
Butyl
355
8.62
0.12
166.64
35.5
4.69
Yes





esters


35
Corn Oil
Butanol
Butyl
355
8.62
0.47
47.43
10
4.74
Yes





esters


36
Corn Oil
Butanol
Butyl
355
8.62
2.8
49.77
11
4.52
No





esters


37
Corn Oil
Butanol
Butyl
355
8.62
0
161.85
35
4.62
Yes





esters


38
Corn Oil
Butanol
Butyl
355
8.62
2.1
55.89
10
5.59
No





esters


39
Corn Oil
Butanol
Butyl
355
8.62
0.12
163.32
35
4.67
Yes





esters


40
Corn Oil
Butanol
Butyl
355
8.62
0.46
45.07
10
4.51
Yes





esters


41
Corn Oil
Butanol
Butyl
355
8.62
2.8
51.47
10
5.15
No





esters


42
Corn Oil
Butanol
Butyl
355
8.62
0.11
167
35
4.77
Yes





esters


43
Corn Oil
Butanol
Butyl
355
8.62
2.54
46.76
10
4.68
No





esters


44
Corn Oil
Propanol
Propyl
340
8.64
0.00
88.56
20
4.428
Yes





esters


45
Corn Oil
Propanol
Propyl
340
8.64
0.00
43.23
10
4.323
Yes





esters


46
Corn Oil
Propanol
Propyl
340
8.64
0.00
43.92
10
4.392
Yes





esters


47
Corn Oil
Propanol
Propyl
340
8.64
0.23
92.32
20
4.616
Yes





esters


48
Corn Oil
Propanol
Propyl
340
8.64
0.23
44.1
10
4.41
Yes





esters


49
Corn Oil
Propanol
Propyl
340
8.64
0.46
44.46
10
4.446
Yes





esters


50
Corn Oil
Propanol
Propyl
340
8.64
0.12
165.76
35
4.736
Yes





esters


51
Corn Oil
Propanol
Propyl
340
8.64
0.12
66
15
4.4
Yes





esters


52
Corn Oil
Propanol
Propyl
340
8.64
1.98
44.05
10
4.405
No





esters


53
Corn Oil
Propanol
Propyl
340
8.64
0.11
90.96
20
4.548
Yes





esters


54
Corn Oil
Propanol
Propyl
340
8.64
0.23
47.77
10
4.777
Yes





esters


55
Corn Oil
Propanol
Propyl
340
8.64
2.80
45.92
10
4.592
No





esters


56
Corn Oil
Propanol
Propyl
340
8.82
0.00
87.43
20.00
4.37
Yes





esters


57
Corn Oil
Propanol
Propyl
340
8.82
0.00
42.87
10.00
4.29
Yes





esters


58
Corn Oil
Propanol
Propyl
340
8.82
0.00
42.68
10.00
4.27
Yes





esters


59
Corn Oil
Propanol
Propyl
340
8.82
0.23
91.88
20.00
4.59
Yes





esters


60
Corn Oil
Propanol
Propyl
340
8.82
0.38
44.24
10.00
4.42
Yes





esters


61
Corn Oil
Propanol
Propyl
340
8.82
0.46
44.85
10.00
4.49
Yes





esters


62
Corn Oil
Propanol
Propyl
340
8.82
0.00
82.88
20.00
4.14
Yes





esters


63
Corn Oil
Propanol
Propyl
340
8.82
0.00
45.10
10.00
4.51
Yes





esters


64
Corn Oil
Propanol
Propyl
340
8.82
0.00
49.38
11.50
4.29
Yes





esters


65
Corn Oil
Propanol
Propyl
340
8.82
0.00
88.89
20.00
4.44
Yes





esters


66
Corn Oil
Propanol
Propyl
340
8.82
0.00
47.67
11.00
4.33
Yes





esters


67
Corn Oil
Propanol
Propyl
340
8.82
0.58
44.91
10.00
4.49
No





esters


68
Corn Oil
Propanol
Propyl
340
9.15
0.12
98.53
20.5
4.81
Yes





esters


69
Corn Oil
Propanol
Propyl
340
9.15
0.12
43.87
10
4.39
Yes





esters


70
Corn Oil
Propanol
Propyl
340
9.15
0.70
44.31
10
4.43
No





esters


71
Corn Oil
Propanol
Propyl
340
9.15
0.12
92.39
20
4.62
Yes





esters


72
Corn Oil
Propanol
Propyl
340
9.15
0.00
44.34
10
4.43
Yes





esters


73
Corn Oil
Propanol
Propyl
340
9.15
0.12
45.49
10
4.55
Yes





esters


74
Corn Oil
Propanol
Propyl
340
9.15
0.12
80.61
20
4.03
Yes





esters


75
Corn Oil
Propanol
Propyl
340
9.15
0.12
56.21
10
5.62
Yes





esters


76
Corn Oil
Propanol
Propyl
340
9.15
0.70
43.48
10
4.35
No





esters


77
Corn Oil
Propanol
Propyl
350
12.51
0.12
96.77
21.5
4.50
Yes





esters


78
Corn Oil
Propanol
Propyl
350
12.51
0.00
46.08
10.5
4.39
Yes





esters


79
Corn Oil
Propanol
Propyl
350
12.51
1.99
48.99
10
4.90
No





esters


80
Corn Oil
Propanol
Propyl
380
12.64
0.12
97.24
23
4.23
Yes





esters


81
Corn Oil
Propanol
Propyl
380
12.64
0.59
44.43
10
4.44
No





esters


82
Corn Oil
Propanol
Propyl
380
12.64
0.11
88.75
20
4.44
Yes





esters


83
Corn Oil
Propanol
Propyl
380
12.64
1.75
43.79
10
4.38
No





esters


84
Corn Oil
Propanol
Propyl
380
12.64
0.23
89.91
20
4.50
Yes





esters


85
Corn Oil
Propanol
Propyl
380
12.64
0.23
40.94
10
4.09
Yes





esters


86
Corn Oil
Propanol
Propyl
380
12.64
1.96
44.47
10
4.45
No





esters


87
Corn Oil
Propanol
Propyl
380
12.64
0.12
89.23
20
4.46
Yes





esters


88
Corn Oil
Propanol
Propyl
380
12.64
0.70
42.73
10
4.27
No





esters


89
Corn Oil
Propanol
Propyl
365
8.64
0.00
84.56
20
4.23
Yes





esters


90
Corn Oil
Propanol
Propyl
365
8.64
0.00
41.55
10
4.16
Yes





esters


91
Corn Oil
Propanol
Propyl
365
8.64
0.00
41.97
10
4.20
Yes





esters


92
Corn Oil
Propanol
Propyl
365
8.61
0.00
83.84
20
4.19
Yes





esters


93
Corn Oil
Propanol
Propyl
365
8.61
0.00
41.02
10
4.10
Yes





esters


94
Corn Oil
Propanol
Propyl
365
8.61
0.35
42.78
10
4.28
Yes





esters


95
Corn Oil
Propanol
Propyl
365
8.44
0.00
89.15
20
4.46
Yes





esters


96
Corn Oil
Propanol
Propyl
365
8.44
0.00
41.31
10
4.13
Yes





esters


97
Corn Oil
Propanol
Propyl
365
8.44
0.00
43.79
10
4.38
Yes





esters


98
Corn Oil
Propanol
Propyl
365
8.51
0.00
88.49
20
4.42
Yes





esters


99
Corn Oil
Propanol
Propyl
365
8.51
0.11
41.23
10
4.12
Yes





esters


100
Corn Oil
Propanol
Propyl
365
8.51
0.23
43.07
10
4.31
Yes





esters


101
Corn Oil
Methanol
Methyl
330
8.59
0.34
112.21
20
5.61
Yes





esters


102
Corn Oil
Methanol
Methyl
330
8.59
0.34
54.56
10
5.46
Yes





esters


103
Corn Oil
Methanol
Methyl
330
8.59
0.92
58.34
10
5.83
No





esters


104
Corn Oil
200 Proof
Ethyl
340
12.89
0.34
118.01
20
5.90
Yes




(HPLC)
esters


105
Corn Oil
200 Proof
Ethyl
340
12.91
0.34
125.44
20
6.27
Yes




(HPLC)
esters


106
Corn Oil
200 Proof
Ethyl
340
12.87
0.11
119.28
20
5.96
Yes




(HPLC)
esters


107
Corn Oil
200 Proof
Ethyl
340
12.87
0.35
116.04
20
5.80
Yes




(HPLC)
esters


108
Corn Oil
200 Proof
Ethyl
340
12.87
0.22
120.39
20
6.02
Yes




(HPLC)
esters


109
Corn Oil
200 Proof
Ethyl
340
18.31
0.57
122.05
20
6.10
No




(HPLC)
esters


110
Corn Oil
200 Proof
Ethyl
340
18.31
0.30
122.95
20
6.15
Yes




(HPLC)
esters


111
Corn Oil
200 Proof
Ethyl
340
18.55
0.40
99.47
20
4.97
Yes




(HPLC)
esters


112
Corn Oil
200 Proof
Ethyl
340
18.04
0.30
93.64
22
4.26
Yes




(HPLC)
esters


113
Corn Oil
200 Proof
Ethyl
340
13.82
0.11
122.54
20
6.13
Yes




(HPLC)
esters


114
Corn Oil
200 Proof
Ethyl
340
13.68
0.11
138.86
20
6.94
Yes




(HPLC)
esters


115
Corn Oil
Methanol
Methyl
325
7.19
0.11
214.89
35
6.14
Yes





esters


116
Corn Oil
Methanol
Methyl
325
7.19
0.58
87.16
15
5.81
No





esters


117
Corn Oil
Methanol
Methyl
325
7.22
0.11
225.69
35
6.45
Yes





esters


118
Corn Oil
Methanol
Methyl
325
7.22
0.46
87.23
15
5.82
Yes





esters


119
Corn Oil
Methanol
Methyl
325
7.22
1.95
56.88
10
5.69
No





esters


120
Corn Oil
Methanol
Methyl
325
7.27
0.11
211.93
35
6.06
Yes





esters


121
Corn Oil
Methanol
Methyl
325
7.27
1.59
95.55
15
6.37
No





esters


122
Corn Oil
Methanol
Methyl
325
7.33
0.23
211.59
35
6.05
Yes





esters


123
Corn Oil
Methanol
Methyl
325
7.33
1.03
89.01
15.5
5.74
No





esters


124
Corn Oil
Methanol
Methyl
325
7.33
0.21
201.16
35
5.75
Yes





esters


125
Corn Oil
Methanol
Methyl
325
7.33
0.79
78.62
15
5.24
No





esters


126
Corn Oil
Methanol
Methyl
325
7.95
0.24
209.69
35
5.99
Yes





esters


127
Corn Oil
Methanol
Methyl
325
7.95
0.35
90.78
15
6.05
Yes





esters


128
Corn Oil
Methanol
Methyl
325
7.95
1.74
61.47
10
6.15
No





esters


129
Corn Oil
Methanol
Methyl
325
4.53
0.23
221.55
35
6.33
Yes





esters


130
Corn Oil
Methanol
Methyl
325
4.53
0.24
91.46
15
6.10
Yes





esters


131
Corn Oil
Methanol
Methyl
325
4.53
0.34
59.82
10
5.98
Yes





esters


132
Corn Oil
Methanol
Methyl
325
3.48
0.23
217.82
35
6.22
Yes





esters


133
Corn Oil
Methanol
Methyl
325
3.48
0.45
88.73
15
5.92
Yes





esters


134
Corn Oil
Methanol
Methyl
325
3.48
2.53
61.39
10
6.14
No





esters


135
Corn Oil
Methanol
Methyl
325
5.00
0.11
210.56
35
6.02
Yes





esters


136
Corn Oil
Methanol
Methyl
325
5.00
0.23
88.44
15
5.90
Yes





esters


137
Corn Oil
Methanol
Methyl
325
5.00
0.66
61.62
10
6.16
No





esters


138
Corn Oil
Methanol
Methyl
325
8.05
0.12
124.52
20
6.23
Yes





esters


139
Corn Oil
Methanol
Methyl
325
8.05
0.11
60.74
10
6.07
Yes





esters


140
Corn Oil
Methanol
Methyl
325
8.05
0.12
57.41
10
5.74
Yes





esters


141
Corn Oil
Methanol
Methyl
325
8.05
0.12
124.52
20
6.23
Yes





esters


142
Corn Oil
Methanol
Methyl
325
8.05
0.12
57.65
10
5.77
Yes





esters


143
Corn Oil
Methanol
Methyl
325
8.05
0.12
58.92
10
5.89
Yes





esters


144
Corn Oil
Methanol
Methyl
325
7.87
0.59
110.82
20
5.54
No





esters


145
Corn Oil
Methanol
Methyl
325
7.93
0.46
54.6
10
5.46
Yes





esters


146
Corn Oil
Methanol
Methyl
325
7.93
0.35
55.03
10
5.50
Yes





esters


147
Corn Oil
Methanol
Methyl
325
8.28
0.12
179.87
30
6.00
Yes





esters


148
Corn Oil
Methanol
Methyl
325
8.28
0.76
130.05
20
6.50
No





esters


149
Corn Oil
Methanol
Methyl
325
8.28
0.13
115.32
20
5.77
Yes





esters


150
Corn Oil
Methanol
Methyl
340
15.06
0.24
202.66
30
6.76
Yes





esters


151
Corn Oil
Methanol
Methyl
340
12.83
0.45
251.64
40
6.29
Yes





esters


152
Soapstock
Methanol
Methyl
320
12.07
0.23
206.92
35
5.91
Yes





esters


153
Soapstock
Methanol
Methyl
320
12.07
0.93
180.92
30
6.03
No





esters


154
Soapstock
Methanol
Methyl
310
2.42
0.34
135.64
25
5.43
Yes





esters


155
Soapstock
Methanol
Methyl
310
5.69
0.22
113.48
20
5.67
Yes





esters


156
Soapstock
Methanol
Methyl
310
5.69
0.23
113.97
20
5.70
Yes





esters


157
Soapstock
Methanol
Methyl
310
5.69
0.00
112.26
20
5.61
Yes





esters


158
Soapstock
Methanol
Methyl
310
5.69
0.35
111.51
20
5.58
Yes





esters


159
Soapstock
Methanol
Methyl
310
5.69
1.06
57.37
10
5.74
No





esters









Example 15
Scale-Up of Continuous Removal of Fatty Acids in Biodiesel Production Process

For this example, the same biodiesel production process was used as described in Example 14 above. However, in this example the fatty acid removal reactor removal reactor (300 mm length by 38.1 mm i.d.) was packed with 150 mesh/58 Å alumina particles (Sigma-Aldrich, St. Louis, Mo.). Also, the fatty acid removal reactor was placed horizontally instead of vertically as described in Example 14. The fatty acid removal reactor was regenerated online by pushing nitrogen through the polisher to displace the biodiesel and alcohol followed by passing air through the polisher at elevated temperature (e.g. 500° C.) to burn/oxidize the adsorbed fatty acids off of the polisher. The polished biodiesel was distilled under vacuum (10 mbar) to remove any residual alcohols and other volatiles. Table 7 below shows the typical regeneration conditions of the fatty acid removal system.




















TABLE 7






Setting
Actual
Setting
Actual
Inlet
Middle
Outlet
Sampling






Temp. 1
Temp. 1
Temp. 2
Temp. 2
Temp.
Temp.
Temp.
Time
N2 Flow
Air Flow


Step
(Celsius)
(Celsius)
(Celsius)
(Celsius)
(Celsius)
(Celsius)
(Celsius)
(min.)
(ml/min)
(ml/min)
Notes


























Heating
500
25
500
25
25
25
25
0
10

Flushing


Heating
500
464
500
501
88
580
126
20
22.5

Flushing


Heating
500
484
500
550
107
598
272
30
23

Flushing


Heating
500
488
500
562
112
600
307
35

16
Burning


Heating
500
496
500
569
118
601
339
37

16
Burning


Heating
500
511
500
560
124
601
361
39

16
Burning


Heating
500
508
500
559
128
596
380
41

16
Burning


Heating
500
508
500
559
132
592
404
42

16
Burning


Heating
500
502
500
560
133
590
428
45

16
Burning


Cooling
OFF
501
OFF
563
135
589
444
46
5

Flushing


Cooling
OFF
126
OFF
227
111
101
241
80
5

Flushing


Cooling
OFF
47
OFF
77
44
60
89
120
5

Flushing









Table 8 below shows that the fatty acid removal system performs quite well to polish biodiesel in order for it to meet the ASTM specification for acid number (acid number not greater than 0.5). Some of the samples that passed the ASTM acid number test were then blended and sent to a third party (FuelOnly, Inc. (ISO9000, Vancouver, Wash.)) for the full battery of ASTM tests applicable to biodiesel under ASTM D6751-07a. This testing revealed that the blended samples passed ASTM specifications for biodiesel fuel.



















TABLE 8












Biodiesel


Collection

Passed



Feed

Biodiesel
Reactor
Acid Number
Biodiesel
Time
Flow
ASTM

















Expt. #
Stock
Alcohol
Type
Temp
Before
After
Collected
(min)
Rate
Acid #?




















160
Corn
190 Proof
Ethyl
390
18.33
0
91.65
40.5
2.26
Yes



oil
Ethanol
esters


161
Corn
190 Proof
Ethyl
390
18.33
0
133.53
40
3.34
Yes



oil
Ethanol
esters


162
Corn
190 Proof
Ethyl
390
18.35
0.12
33.92
10
3.39
Yes



oil
Ethanol
esters


163
Corn
190 Proof
Ethyl
390
18.35
0.12
33.02
10
3.30
Yes



oil
Ethanol
esters


164
Corn
190 Proof
Ethyl
400
17.88
0.24
141.68
40.5
3.50
Yes



oil
Ethanol
esters


165
Corn
190 Proof
Ethyl
400
17.88
0.12
131.3
40
3.28
Yes



oil
Ethanol
esters


166
Corn
190 Proof
Ethyl
400
17.88
0.12
66.08
20
3.30
Yes



oil
Ethanol
esters


167
Corn
190 Proof
Ethyl
400
17.88
0.24
35.1
10
3.51
Yes



oil
Ethanol
esters


168
Corn
190 Proof
Ethyl
400
18.71
0.12
138.35
40
3.46
Yes



oil
Ethanol
esters


169
Corn
190 Proof
Ethyl
400
18.71
0.12
131.49
40
3.29
Yes



oil
Ethanol
esters


170
Corn
190 Proof
Ethyl
400
18.71
0.24
65.87
20
3.29
Yes



oil
Ethanol
esters


171
Corn
190 Proof
Ethyl
400
18.71
0.12
67.14
20
3.36
Yes



oil
Ethanol
esters


172
Corn
190 Proof
Ethyl
400
18.71
0.24
65.92
20
3.30
Yes



oil
Ethanol
esters


173
Corn
190 Proof
Ethyl
400
18.71
0.24
65.6
20
3.28
Yes



oil
Ethanol
esters


174
Corn
190 Proof
Ethyl
400
18.71
1.31
70.18
21
3.34
No



oil
Ethanol
esters


175
Corn
190 Proof
Ethyl
400
17.46
0.00
137.45
40
3.44
Yes



oil
Ethanol
esters


176
Corn
190 Proof
Ethyl
400
17.46
0.12
131.45
40.5
3.25
Yes



oil
Ethanol
esters


177
Corn
190 Proof
Ethyl
400
17.46
0.12
65.13
20
3.26
Yes



oil
Ethanol
esters


178
Corn
190 Proof
Ethyl
400
17.46
0.12
65.58
20
3.28
Yes



oil
Ethanol
esters


179
Corn
190 Proof
Ethyl
400
17.46
0.00
64.57
20
3.23
Yes



oil
Ethanol
esters


180
Corn
190 Proof
Ethyl
400
17.46
0.24
65.47
20
3.27
Yes



oil
Ethanol
esters


181
Corn
190 Proof
Ethyl
400
17.46
0.96
33.24
10
3.32
No



oil
Ethanol
esters


182
Corn
190 Proof
Ethyl
400
17.46
2.15
34.77
10
3.48
No



oil
Ethanol
esters


183
Corn
190 Proof
Ethyl
400
17.2
0.00
137.88
40
3.45
Yes



oil
Ethanol
esters


184
Corn
190 Proof
Ethyl
400
17.2
0.12
137.35
40
3.43
Yes



oil
Ethanol
esters


185
Corn
190 Proof
Ethyl
400
17.2
0.12
135.1
42
3.22
Yes



oil
Ethanol
esters


186
Corn
190 Proof
Ethyl
400
17.2
0.12
66.18
20
3.31
Yes



oil
Ethanol
esters


187
Corn
190 Proof
Ethyl
400
17.2
0.47
65.92
20
3.30
Yes



oil
Ethanol
esters


188
Corn
190 Proof
Ethyl
400
17.2
1.43
33.23
10
3.32
No



oil
Ethanol
esters


189
Corn
190 Proof
Ethyl
400
17.48
0.36
130.68
40
3.27
Yes



oil
Ethanol
esters


190
Corn
190 Proof
Ethyl
400
17.48
1.80
39.55
12
3.30
No



oil
Ethanol
esters


191
Corn
Recovered
Ethyl
400
21.57
0.11
137.94
40
3.45
Yes



oil
Ethanol
esters


192
Corn
Recovered
Ethyl
400
21.57
0.33
121.31
40
3.03
Yes



oil
Ethanol
esters


193
Corn
Recovered
Ethyl
400
21.57
3.03
63.37
20
3.17
No



oil
Ethanol
esters









The invention has been described with reference to various specific and preferred embodiments and techniques. However, it should be understood that many variations and modifications may be made while remaining within the spirit and scope of the invention.


It should be noted that, as used in this specification and the appended claims, the singular forms “a,” “an,” and “the” include plural referents unless the content clearly dictates otherwise. Thus, for example, reference to a composition containing “a compound” includes a mixture of two or more compounds. It should also be noted that the term “or” is generally employed in its sense including “and/or” unless the content clearly dictates otherwise.


It should also be noted that, as used in this specification and the appended claims, the phrase “configured” describes a system, device, or other structure that is constructed or configured to perform a particular task or adopt a particular configuration. The phrase “configured” can be used interchangeably with other similar phrases such as arranged and configured, constructed and arranged, constructed, manufactured and arranged, and the like.


All publications and patent applications in this specification are indicative of the level of ordinary skill in the art to which this invention pertains. All publications and patent applications are herein incorporated by reference to the same extent as if each individual publication or patent application was specifically and individually indicated by reference.

Claims
  • 1. A system for producing a refined oil product comprising: a production reactor for producing a crude oil product mixture, the reactor comprising a lipid reservoir, and an alcohol reservoir; anda first organic acid removal reactor in fluid communication with the production reactor, the first organic acid removal reactor comprising a first housing defining an interior volume, the housing configured to receive the crude oil product mixture from the production reactor, metal oxide media disposed within the interior volume of the removal reactor housing, the metal oxide media comprising a metal oxide selected from the group consisting of zirconia, alumina, hafnia, and titania.
  • 2. The system of claim 1, the first housing comprising an input port and an output port; the first organic acid removal reactor further comprising a temperature control unit configured to maintain the temperature within the first housing within a first temperature range for a first period of time and within a second temperature range for a second period of time following the first period, the second range higher than the first range.
  • 3. The system of claim 1, the metal oxide media comprising particles from 0.2 um to 2 mm.
  • 4. The system of claim 2, further comprising further comprising a sensor in fluid communication with the output port, the sensor configured to determine the concentration of organic acids in a sample composition.
  • 5. The system of claim 4, the sensor comprising a pH sensor.
  • 6. The system of claim 1, further comprising a second organic acid removal reactor and control valves, wherein actuation of the control valves causes the second organic acid removal reactor to be in fluid communication with the production reactor instead of the first organic acid removal reactor.
Parent Case Info

This application claims the benefit of U.S. Provisional Application No. 60/889,730, filed Feb. 13, 2007, and U.S. Provisional Application No. 60/945,083, filed Jun. 19, 2007, the contents of all of which are herein incorporated by reference in their entirety.

US Referenced Citations (107)
Number Name Date Kind
2383632 Trent Aug 1945 A
2679471 Ayers et al. May 1954 A
3383396 Cahn et al. May 1968 A
4138336 Mendel et al. Feb 1979 A
4216337 Baba et al. Aug 1980 A
4487933 Mixan et al. Dec 1984 A
4582589 Ushizawa et al. Apr 1986 A
4716218 Chen et al. Dec 1987 A
4861739 Pellet et al. Aug 1989 A
5108597 Funkenbusch et al. Apr 1992 A
5179219 Priegnitz Jan 1993 A
5182016 Funkenbusch et al. Jan 1993 A
5252762 Denton et al. Oct 1993 A
5254262 Funkenbusch et al. Oct 1993 A
5271833 Funkenbusch et al. Dec 1993 A
5298650 Walter et al. Mar 1994 A
5321197 Angstadt et al. Jun 1994 A
5346619 Funkenbusch et al. Sep 1994 A
5350879 Engel et al. Sep 1994 A
5389240 Gillespie et al. Feb 1995 A
5508457 Bayense et al. Apr 1996 A
5532392 Gheorghiu Jul 1996 A
5540834 Carr et al. Jul 1996 A
5908946 Stern et al. Jun 1999 A
5985137 Ohsol et al. Nov 1999 A
6090959 Hirano et al. Jul 2000 A
6211390 Peter et al. Apr 2001 B1
6376701 Chavan et al. Apr 2002 B1
6392062 Haas May 2002 B1
6433146 Cheryan Aug 2002 B1
6489496 Barnhorst et al. Dec 2002 B2
6538146 Turck Mar 2003 B2
6666074 Gerner et al. Dec 2003 B2
6712867 Boocock Mar 2004 B1
6719815 Nanninga et al. Apr 2004 B2
6768015 Luxem et al. Jul 2004 B1
6878837 Bournay et al. Apr 2005 B2
6887283 Ginosar et al. May 2005 B1
6960672 Nakayama et al. Nov 2005 B2
6963004 Ahtchi-Ali et al. Nov 2005 B2
6965044 Hammond et al. Nov 2005 B1
6979426 Teall et al. Dec 2005 B2
6982340 Mumura et al. Jan 2006 B2
7045100 Ergün et al. May 2006 B2
7097770 Lysenko Aug 2006 B2
7112688 Tysinger et al. Sep 2006 B1
7145026 Fleisher Dec 2006 B2
7151187 Delfort et al. Dec 2006 B2
7211681 Furuta May 2007 B2
7321052 Miller et al. Jan 2008 B2
7498454 Relingshoefer Mar 2009 B2
7514657 Moreira et al. Apr 2009 B2
7563915 Matson Jul 2009 B2
7582784 Banavali et al. Sep 2009 B2
7601858 Cantrell et al. Oct 2009 B2
7635398 Bertram et al. Dec 2009 B2
7790651 Lin Sep 2010 B2
7897798 McNeff Mar 2011 B2
8017796 McNeff et al. Sep 2011 B2
8445709 McNeff et al. May 2013 B2
20020010359 Kaita et al. Jan 2002 A1
20020156305 Turck Oct 2002 A1
20030229238 Fleisher Dec 2003 A1
20040074760 Portnoff et al. Apr 2004 A1
20040087809 Nakayama et al. May 2004 A1
20040094477 Lysenko et al. May 2004 A1
20050006290 Patten Jan 2005 A1
20050064577 Berzin Mar 2005 A1
20050080280 Yoo Apr 2005 A1
20050118409 McNeff et al. Jun 2005 A1
20050137411 Ahtchi-Ali et al. Jun 2005 A1
20050204612 Connemann et al. Sep 2005 A1
20050239182 Berzin Oct 2005 A1
20050260553 Berzin Nov 2005 A1
20050261509 Delfort et al. Nov 2005 A1
20050266139 Lacome et al. Dec 2005 A1
20050274065 Portnoff et al. Dec 2005 A1
20060014974 Bournay et al. Jan 2006 A1
20060041152 Cantrell et al. Feb 2006 A1
20060041153 Cantrell et al. Feb 2006 A1
20060043003 Moreira et al. Mar 2006 A1
20060080891 Ghosh et al. Apr 2006 A1
20060149087 Furuta Jul 2006 A1
20060224005 Felly Oct 2006 A1
20060252950 Ginosar et al. Nov 2006 A1
20060260186 Iversen et al. Nov 2006 A1
20060288636 Iijima et al. Dec 2006 A1
20070010682 Myllyoja et al. Jan 2007 A1
20070027338 Furuta Feb 2007 A1
20070037994 Canos et al. Feb 2007 A1
20070066838 Hillion et al. Mar 2007 A1
20070089356 Krasutsky et al. Apr 2007 A1
20070093380 Srinivas et al. Apr 2007 A1
20070196892 Winsness et al. Aug 2007 A1
20070282118 Gupta et al. Dec 2007 A1
20070283619 Hillion et al. Dec 2007 A1
20080161615 Chapus Jul 2008 A1
20080188676 Anderson et al. Aug 2008 A1
20080318763 Anderson Dec 2008 A1
20090029445 Eckelberry et al. Jan 2009 A1
20090126262 Asthana et al. May 2009 A1
20100087670 Wang et al. Apr 2010 A1
20100147771 McNeff et al. Jun 2010 A1
20100170143 McNeff et al. Jul 2010 A1
20100170147 McNeff et al. Jul 2010 A1
20100191004 McNeff et al. Jul 2010 A1
20110060153 Mcneff et al. Mar 2011 A1
Foreign Referenced Citations (63)
Number Date Country
8202429 Nov 1983 BR
1680514 Oct 2005 CN
1718679 Jan 2006 CN
1858160 Nov 2006 CN
1887417 Jan 2007 CN
1928016 Mar 2007 CN
102005038137 Feb 2007 DE
0198243 Oct 1986 EP
0507217 Oct 1992 EP
0535290 Apr 1993 EP
1505048 Feb 2005 EP
1580255 Sep 2005 EP
1607467 Dec 2005 EP
1681281 Jul 2006 EP
2188612 Jan 1974 FR
2679471 Jan 1993 FR
2890656 Mar 2007 FR
2132222 Jul 1984 GB
6313188 Nov 1994 JP
11228494 Aug 1999 JP
2005126346 May 2005 JP
2005-177722 Jul 2005 JP
2007153943 Jun 2007 JP
2007190450 Aug 2007 JP
2008111085 May 2008 JP
WO 0005327 Feb 2000 WO
WO-03062358 Jul 2003 WO
WO-03087279 Oct 2003 WO
WO-03094598 Nov 2003 WO
WO-2004085585 Oct 2004 WO
WO-2004096962 Nov 2004 WO
WO-2005000782 Jan 2005 WO
WO 2005021697 Mar 2005 WO
WO-2005035479 Apr 2005 WO
WO-2005093015 Oct 2005 WO
WO-2005123890 Dec 2005 WO
WO-2006081644 Aug 2006 WO
WO-2006088254 Aug 2006 WO
WO-2006093896 Sep 2006 WO
WO-2006094986 Sep 2006 WO
WO-2007011343 Jan 2007 WO
WO-2007012190 Feb 2007 WO
WO-2007025360 Mar 2007 WO
WO-2007029851 Mar 2007 WO
WO-2007038605 Apr 2007 WO
WO-2007043062 Apr 2007 WO
WO-2007072972 Jun 2007 WO
WO-2006070661 Jul 2007 WO
WO-2007077950 Jul 2007 WO
WO-2007111604 Oct 2007 WO
WO-2007140395 Dec 2007 WO
WO-2007141293 Dec 2007 WO
WO-2007142983 Dec 2007 WO
WO-2008012275 Jan 2008 WO
WO-2008019325 Feb 2008 WO
WO-2008034109 Mar 2008 WO
WO-2008029132 Mar 2008 WO
WO-2008041038 Apr 2008 WO
WO-2008101032 Aug 2008 WO
WO-2009002880 Dec 2008 WO
WO-2009007234 Jan 2009 WO
WO-2009007234 Jan 2009 WO
WO-2010144597 Dec 2010 WO
Non-Patent Literature Citations (85)
Entry
“Mexico Office Action”, from MX Application No. MX/a/2009/008612, mailed Jul. 11,2012, (pp. 1-4) Including English translation.
“PCT Notification Concerning Transmittal of International Preliminary Report on Patentability”, from International Application No. PCT/US2010/38000, corresponding to U.S. Appl. No. 61/185,453, mailed Dec. 22, 2011, pp. 1-6.
“Restriction Requirement Received”, mailed Sep. 5, 2012 in U.S. Appl. No. 12/797,393, “Systems and Methods for Refining Alkyl Ester Compositions,” (5 pages).
PCT International Search Report and Written Opinion from International Application No. PCT/US2007/075211, mailed Jul. 9, 2008 (pp. 1-14).
“EP Communication, EPO form 2906 01.91TRI, from the European Patent Office in EP Patent Application No. 07840692.3, corresponding to U.S. Appl. No. 11/833,839, mailed Dec. 11, 2009, (pp. 1-4)”.
“EP Communication, EPO form 2906 01.91TRI, from the European Patent Office in EP Patent Application No. 08729792.5, corresponding to U.S. Appl. No. 12/030,801, mailed Mar. 2, 2010, (pp. 1-4)”.
File History for co-pending U.S. Appl. No. 12/238,750, “Methods and Compositions for Refining Lipid Feed Stocks,” (168 pages).
File History for co-pending U.S. Appl. No. 12/540,568, “Systems For Selective Removal of Contaminants From a Composition and Methods of Regenerating the Same,” (117 pages).
“Kyte Centrifuge Sales & Consulting”, www.kcentrifude.com , p. 1.
“PCT International Search Report and Written Opinion from International Application No. PCT/US2010/038000, corresponding to U.S. Appl. No. 12/797,393, mailed Oct. 4, 2010, pp. 1-13”.
“PCT Notification Concerning Transmittal of International Preliminary Report on Patentability”, From International Application No. PCT/US2007075211, corresponding to U.S. Appl. No. 11/833,839, mailed Feb. 19, 2009, pp. 1-9.
“PCT Notification Concerning Transmittal of International Preliminary Report on Patentability”, From International Application No. PCT/US2008053883, corresponding to U.S. Appl. No.12/030,801, mailed Aug. 27, 2009, pp. 1-9.
“Response to European Communication pursuant to Article 94 (3) EPC, dated Dec. 11, 2009, Filed in the European Patent Office on Jun. 16, 2009 for EP Patent Application No. 07840692.3, corresponding to U.S. Appl. No. 11/833,839, (1-12)”.
Annen, et al., “Development of Porous Zirconia Spheres by Polymerization-Induced Colloid Aggregation-Effect of Polymerization Rate”, Journal of Mater. Sci., 29(23):6123-6130 (1994).
Anon, , “Beatrice Biodiesel Selects Axens Exterfip-H Technology”, Biodiesel Magazine Jun. 2006, Unknown.
BCC Research, “Global Market for Catalyst Regeneration”, MarketResearch.com http://www.marketresearch.com/product/display.asp?productid=1354464 2006 , 1-20.
Blackwell, J. A. et al., “A Chromatographic Study of the Lewis Acid-Base Chemistry of Zirconia Surfaces”, J. Liquid Chromatog. 1991 , 14: 2875-2889.
Blackwell, J. A. et al., “Study of the Fluoride Adsorption Characterisitics of Porous Microparticulate Zirconium Oxide”, J. Chromatog. 1991 , 549: 43-57.
Bournay, L. et al., “New Heterogeneous Process for Biodiesel Production: A Way to Improve the Quality and the Value of the Crude Glycerin Produced by Biodiesel Plants”, Catalysis Today 2005 , 106: 190-192.
Brown, Adrian S. et al., “Sulfated Metal Oxide Catalysts: Superactivity through Superacidity?”, Green Chemistry Feb. 1999 , 17-20.
Bryan, Tom , “Adsorbing It All”, Biodiesel Magazine Mar. 2005 , 40-43.
Cao, W. et al., “Preparation of Biodiesel from Soybean Oil Using Supercritical Methanol and Co-Solvent”, Fuel 2005 , 84: 347-351.
Collins, K. , “Statement of Keith Collins, Chief Economist, U.S. Department of Agriculture before the U.S. Senate Committee on Appropriations, Subcommittee on Agriculture, Rural Development, and Related Agencies: Economic Issues Related to Biofuels.”, Unknown www.usda.gov/documents/Farmbill07energy.doc. Aug. 26, 2006 , 1-8 (web).
Dean, Morgan et al., “Nanocrystalline Metal Oxide-Based Catalysts for Biodiesel Production from Soybean Oil”, #96—Student Poster Session: Catalysis & Reaction Engineering http://aiche.confex.com/aiche/2006/techprogram/P78366.HTM Nov. 13, 2006 , 1 (web).
Demirbas, Ayhan , “Biodiesel fuels from vegetable oils via catalytic and non-catalytic supercritical alcohol transesterifications and other methods: a survey”, Energy Conversion & Management 2003 , issue 44 pp. 2093-2109.
Di Serio, et al., “Synthesis of Biodiesel via Homogeneous Lewis Acid Catalyst”, J. Molec. Catal. A Chem. 2005 , 239: 111-115.
Di Serio, M. et al., “Transesterification of Soybean Oil to Biodiesel by Using Heterogeneous Basic Catalysts”, Ind. Eng. Chem. Res. 2006 , 45: 3009-3014.
Dorsa, Renato et al., “Basics of Alkali Refining of Vegetable O”, GEA Westfalia Separator Food Tec GmbH Unknown , 1-28.
Dunlap, C. J. et al., “Zirconia Stationary Phases for Extreme Separations”, Anal. Chem. 2001 , 73: 598A-607A.
Elliott, Brian , “Low-cost Biodiesel Production Process Using Waste Oils and Fats”, U.S. EPA SBIR Phase I Kick-Off Meeting www.iastate.edu/Inside/2003/0613/biorenewable.jpg Apr. 5. 2007 , 1.
Fabbri, D. et al., ““Dimethyl carbonate as anovel methylating reagent for fatty acidsin analytical pyrolysis””, Journal of Chromatography, Elsevier Science Publishers B.V, NL LNKDDOI:l0.l016/J.CHROMA.2004.12.077 Feb. 18, 2005.
Furuta, S. et al., “Biodiesel Fuel Production with Solid Superacid Catalysis is Fixed Bed Reactor Under Atmospheric Pressure”, Catalysis Communications 2004 , 5: 721-723.
Gercel, H. F. et al., “Hydropyrolysis of Extracted Euphorbia rigida in a Well-Swept Fixed-Bed Tubular Reactor”, Energy Sources 2002 , 24: 423-430.
Goering, C. E. et al., “Fuel Properties of Eleven Vegetable Oils”, Trans ASAE 1982 , 25: 1472-1477.
Goodwin, J. G. , “Research Activities: Biodiesel Synthesis”, Chemical and Biomolecular Engineering at Clemson University http:/www.ces.clemson.edu/chemeng/facultypages/goodwin/research.html 2006, 1-5.
Haas, M. J. et al., “Engine Performance of Biodiesel Fuel Prepared from Soybean Soapstack: A High Quality Renewable Fuel Produced from a Waste Feedstock”, Energy Fuels 2001 , 15: 1207-1212.
Haas, M. J. et al., “Improving the Economics of Biodiesel Production Through the Use of Low Value Lipids as Feedstocks: Vegetable Oil soapstock”, Fuel Process. Technol. 2005 , 86: 1087-1096.
Harvey, A. P. et al., “Process Intensification of Biodiesel Production Using a Continuous Oscillatory Flow Reactor”, J. Chem. Technol. Biotechnol. 2003 , 78: 338-341.
He, Chen et al., “Biodiesel from Transesterification of Cotton Seed Oil by Solid Bases Catalysis”, Journal of Chemical Engineering of Chinese Universities Aug. 2006 , No. 4 vol. 20.
He, Chen et al., “Biodiesel Production by the transesterification of cottonseed oil by solid acid catalysts”, Frontiers of Chemical Engineering in China Feb. 2006 , vol. 1, No. 1, pp. 1673-7369.
Henry, R. A. et al., “A Novel Chemical Route to Stable, Regenerable Zirconia-Based Chiral Stationary Phases for HPLC”, American Laboratory (News Edition) 2005 , 37: 22-24.
Hill, J. et al., “Environmental, Economic, and Energetic Costs and Benefits of Biodiesel and Ethanol Biofuels”, PNAS 2006 , 103(30): 11206-11210.
Iijima, Wataru et al., ““Winterized” Bio-Diesel Fuel Produced from Animal Fat”, Agro-Energy Laboratory, Dept. of Farm Mechanization and Engineering,National Agricultural ResearchCentre, National Agricultural Research Organization, Japan Unknown , 1-2.
Iijima, Wataru et al., “The Non-glycerol Process of Biodiesel Fuel Treated in Supercritical Methanol (Abstract)”, Paper No. 046073, 2004 ASAE Annual Meeting 2004 , 1.
Ishihara, K. et al., “Direct Ester Condensation from a 1:1 Mixture of Carboxylic Acids and Alcohols Catalyzed by Hafnium (IV) or Zirconium (IV) Salts.”, Tetrahedron 2002 , 58: 8179-8188.
Kahn, A. , “Research into Biodiesel Catalyst Screening and Development”, Thesis, University of Queensland Brisbane 2002 , 1-41.
Kiss, Anton A. et al., “Solid Acid Catalysts for Biodiesel Production—Towards Sustainable Energy”, Adv. Synth. Catal. 2006 , 348: 75-81.
Knothe, G. , “Analytical Methods Used in the Production and Fuel Quality Assessment of Biodiesel”, Transactions of the ASAE 2001 , 44(2): 193-200.
Knothe, Gerhard et al., “Bidiesel: The Use of Vegetable Oils and Their Derivatives as Alternative Diesel Fuels”, Oil Chemical Research, National Center for Agricultural Utilization Research, Agricultural Research Service, U.S. Department of Agriculture, Peoria, IL 61604 Unknown , 1-36.
Koh, Ashley D. , “Non-Catalytic Biodiesel Production from Soybean Oil Using Supercritical Methanol”, The 2006 Annual Meeting San Francisco, CA http://aiche.confex.com/aiche/2006/techprogram/P69978.HTM presented Nov. 15, 2006 , 1.
Kulkarni, Mangesh G. et al., “Solid Acid Catalyxed Biodiesel Production by Simultaneous Esterification and Transesterification”, Green Chem. 2006 , 8:.1056-1062.
Kulkarni, M. et al., “Waste Cooking Oil: An Economical Source for Biodiesel”, Ind. Eng. Chem. Res. 2006 , 45: 2901-2913.
Liu, Yijun et al., “Transesterification of Poultry Fat with Methanol Using Mg—Al Hydrotalcite Derived Catalysts”, Applied Catalysis A: General (Abstract only).2007 , vol. 331, 138-148.
Lopez, Dora E. et al., “Esterification and transesterification on tungstated zirconia: Effect of calcination temperature”, Journal or Catalysis Apr. 1, 2007 , vol. 247, Iss. 1, 43-50.
Lopez, D.E. et al., “Transesterification of Triacetin with Methanol on Solid Acid and Base Catalysts”, Appl. Catalysis A: General 2005 , 295: 97-105.
Lotero, E. et al., “Synthesis of Biodiesel Via Acid Catalysis”, Ind. Eng. Chem. Res. 2005 , 44:5353-5363.
Ma, R et al., “Biodiesel Production: A Review”, Bioresource Technol. 1999 , 70:1-15.
Miller, Dennis J. et al., “Catalysis for Biorenewables Conversion”, National Science Foundation Workshop Report www.egr.msu.edu/apps/nsfworkshop Apr. 13, 2004 , 1-63 (web).
Mittelbach, Martin et al., “Diesel Fuel Derived from Vegetable Oils, III. Emission Tests Using Methyl Esters of Used Frying Oil”, JAOCS Jul. 1988 , vol. 65, No. 7, 1185-1187.
Nawrocki, J. et al., “Chemistry of Zirconia and Its Use in Chromatography”, J. Chromatog. 1993 , A 657: 229-282.
Omota, F. et al., “Fatty Acid Esterification by Reactive Distillation: Part 2—Kinetics-based Design for Sulphated Zirconia Catalysts”, Chemical Engineering Science 2003 , 58: 3175-3185.
Ondrey, G. , “Biodiesel Production Using a Heterogeneous Catalyst”, Chemical Engineering 2004 , 111(11):13.
Otera, J. , “Transesterification”, Chem. Rev. 1993 , 93:1449-1470.
Peterson, C. L. et al., “Continuous Flow Biodiesel Production”, Appl. Eng. Agricul. 2002 , 18: 5-11.
Pinto, A. C. et al., “Biodiesel: An Overview”, J. Braz. Chem. Soc. 2005 , 16:.1313-1330.
Pruszko, R. , “Strategic Biodiesel Decisions”, Iowa State University—University Extension CIRAS 2006 , 1-32.
Raddi De Araujo, Lucia R. et al., “H3PO4/Al2O3 Catatysts: Characterization and Catalytic Evaluation of Oleic Acid Conversion to Biofuels and Biolubricant”, Materials Research 2006 , vol. 9, No. 2, 181-184.
Reisch, Marc S. , “Start-up Firms Pursue Biofuels”, Chemical & Engineering News Nov. 20, 2006 , vol. 84, No. 47, 1-2(web).
Rigney, M. P. et al., “Physical and Chemical Characterization of Microporous Zirconia”, J. Chromatog 1990 , 499: 291-304.
Robichaud, Michael J. et al., “An Improved Oil Emulsion Synthesis Method for Large, Porous Zirconia Particles for Packed- or Fluidized-Bed Protein Chromatography”, Separation Science and Technology 1997 , 32(15), pp. 2547-2559.
Schuchardt, Ulf et al., “Transesterification of Vegetable Oils: a Review”, J. Braz. Chem. Soc. 1998 , vol. 9, No. 1, 199-210.
Silva, Lisa et al., “Colorado Diesel School Bus Retrofit Program”, A Cooperative Effort of the Regional Air Quality Council and the Colorado.Department of Public Health and Environment 2006 , 1-17.
Suppes, G. J. et al., “Transesterification of Soybean Oil with Zeolite and Metal Catalysts”, Applied Catalysis A: General 2004 , 257: 213-223.
Suwannakarn, Kaewta et al., “A comparative study of gas phase esterification on solid acid catalysts”, Catalysis Letters Apr. 2007 , vol. 114, Nos. 3-4, 1-7.
Tyson, K. S. , “Brown Grease Feedstocks for Biodiesel”, National Renewable Energy Laboratory Jun. 19, 2002 , 1-34.
Unknown, “AMBERLITEtm FP Ion Exchange Resins”, Amberlite FP technical bulletin http://www.advancedbiosciences.com Dec. 2004 , 1-7.
Unknown, et al., “Oak Ridge lab develops materials for biodiesel catalysis”, Biodiesel Magazine http://biodieselmagazine.com/article-print.jsp?article—id=1580 2007 , 1.
Unknown, “Standard Test Method for Acid Number of Petroleum Products by Potentiometric Titration”, ASTM International, Designation: D664-04 Mar. 2004 , 1-7.
Verkade, J. G. et al., “Nanoporous Solid Catalysts for Conversion of Soybean Oil to Biodiesel”, Center for Catalysis, Iowa State University http://www.iprt.iastate.edu/ccat/nano.html Feb. 22, 2006 , 1-4.
Vieitez, Ignacio et al., “Continuous Production of Soybean Biodiesel in Supercritical Ethanol-Water Mixtures”, American Chemical Society, Energy & Fuels Jun. 17, 2008 , pp. 1-5.
Xie, W. et al., “Synthesis of Biodiesel from Soybean Oil Using Heterogeneous KF/ZnO Catalyst”, Catalyst Letters Feb. 2006 , 107: 53-59.
Yokoyama, Shin-Ya et al., “Liquid Fuel Production from Ethanol Fermentation Stillage”, Chemistry Letters 1986 , pp. 649-652.
Zhang, P. , “A New Process for Biodiesel Production Based on Waste Cooking Oils and Heterogeneous Catalysts”, USDA-SBIR Agreement #2005-33610-15497 2005 , 1-2.
“Notice of Allowance”, Mailed May 11, 2011 in co-pending U.S. Appl. No. 12/540,568, “Systems for Selective Removal of Contaminants From a Composition and Methods of Regenerating the Same” (20 pages).
PCT International Search Report mailed Jul. 9, 2008 for PCT/US2008/053883.
Related Publications (1)
Number Date Country
20080197052 A1 Aug 2008 US
Provisional Applications (2)
Number Date Country
60889730 Feb 2007 US
60945083 Jun 2007 US