MATERIALS AND METHODS FOR THE SELECTIVE RECOVERY OF MULTIVALENT PRODUCTS

Abstract

Described herein are processes and apparatus for the high purity and high concentration recovery of multivalent products via continuous ion exchange from aqueous solutions for further down-stream purification.

Claims

1. A method of recovering multivalent products from aqueous solutions using continuous ion exchange comprising; (a) adsorbing the multivalent product principally as divalent specie onto an ion exchange resin; (b) converting the adsorbed multivalent product to principally the monovalent valence state; (c) concentrating the multivalent product through re-adsorption onto the ion exchange resin; and (d) eluting the multivalent product.

2. The method of claim 1, wherein the multivalent product is chosen from dicarboxylic acids and diamines.

3. The method of claim 2, wherein the dicarboxylic acids are chosen from succinic acid, glutaric acid, adipic acid, and pimelic acid.

4. The method of claim 2, wherein the diamines are chosen from putrescine, cadaverine, hexamethylenediamine, and heptamethylenediamine.

5. The method of claim 1, wherein (1) impurities are selectively desorbed and (2) the adsorbed multivalent product is converted to principally the monovalent state by feeding a base or an acid at a concentration that allows the pH of the aqueous solution discharged from the resin to be approximately the pK.sub.a2 for cationic divalent products and to be approximately the pK.sub.a1 for anionic divalent products.

6. The method of claim 5, wherein multivalent product at a pH of approximately the first equivalence point is recycled to the ion exchange resin and concentrated through re-adsorption.

7. The method of claim 1, wherein (1) impurities are selectively desorbed and (2) the adsorbed multivalent product is converted to principally the monovalent state by recycling multivalent product in principally the zero valence state, concentrating the multivalent product though re-adsorption.

8. The method of claim 1, wherein the multivalent product is eluted from the ion exchange resin with a high concentration of ammonia, ammonium bicarbonate and/or ammonium carbonate.

9. The method of claim 6 or claim 8, where the eluted multivalent product is fed to a steam stripper, adjusting the pH of the multivalent product to approximately the first equivalence point.

10. The method of claim 7 or claim 8, where the eluted multivalent product is fed to a steam stripper, adjusting the pH to where the multivalent product is principally in the zero valence state.

11. The method of claim 9 or claim 10, where a fraction of the multivalent product recovered from the steam stripper is recycled to the ion exchange resin and concentrated through re-adsorption.

12. The method of claim 1, further comprising at least one wash step after one or more of steps (a), (b), (c), and (d) using an aqueous solution.

13. An apparatus for recovering multivalent products from aqueous solutions comprising one or more of the below zones: (a) an adsorption zone comprising an ion exchange resin, for adsorption of the multivalent product as principally a divalent specie; (b) a monovalent strip zone, for desorbing impurities and converting the adsorbed multivalent product to the monovalent state; (c) a monovalent adsorption zone, for adsorbing recycled multivalent product recycled from a steam stripper; and (d) an elution zone, for eluting the multivalent product using a concentrated ammonia, ammonium bicarbonate or ammonium carbonate solution.

14. The apparatus according to claim 13, wherein the multivalent product is chosen from dicarboxylic acids and diamines.

15. The apparatus according to claim 14, wherein the dicarboxylic acids are chosen from succinic acid, glutaric acid, adipic acid, and pimelic acid.

16. The apparatus according to claim 14, wherein the diamines are chosen from putrescine, cadaverine, hexamethylenediamine, and heptamethylenediamine.

17. The apparatus of claim 13, which is configured to selectively desorb impurities and (2) to convey the adsorbed multivalent product to principally the monovalent state by feeding a base or an acid at a concentration that allows the pH of the aqueous solution discharged from the resin to be approximately the pK.sub.a2 for cationic divalent products and to be approximately the pK.sub.a1 for anionic divalent products.

18. The apparatus of claim 17, wherein multivalent product at a pH of approximately the first equivalence point is recycled to the ion exchange resin and concentrated through re-adsorption.

19. The apparatus of claim 13, wherein (1) impurities are selectively desorbed and (2) the adsorbed multivalent product is converted to principally the monovalent state by recycling multivalent product in principally the zero valence state, concentrating the multivalent product though re-adsorption.

20. The apparatus of claim 13, wherein the multivalent product is eluted from the ion exchange resin with a high concentration of ammonia, ammonium bicarbonate and/or ammonium carbonate.

21. The apparatus of claim 18 or claim 20, where the eluted multivalent product is fed to a steam stripper, adjusting the pH of the multivalent product to approximately the first equivalence point.

22. The apparatus of claim 19 or claim 20, where the eluted multivalent product is fed to a steam stripper, adjusting the pH to where the multivalent product is principally in the zero valence state.

23. The apparatus of claim 21 or claim 22, where a fraction of the multivalent product recovered from the steam stripper is recycled to the ion exchange resin and concentrated through re-adsorption.

24. The apparatus of claim 13, further comprising at least one elution wash zone after one or more of zones (a), (b), (c), and (d) using an aqueous solution.

25. The apparatus of claim 13, wherein the monovalent strip zone and the monovalent adsorption zone are combined.

Description

DESCRIPTION OF DRAWINGS

[0020] FIG. 1 is a schematic of an exemplary continuous ion exchange unit operation containing a separate Monovalent Strip Zone and a separate Monovalent Adsorption Zone, leading to the high purity and high concentration recovery of multivalent products prior to further purification.

[0021] FIG. 2 is a schematic of an exemplary continuous ion exchange unit operation containing a combined Monovalent Strip Zone and a Monovalent Adsorption Zone, leading to the high purity and high concentration recovery of multivalent products prior to further purification.

[0022] FIG. 3 tabulates the experimental results from an Akta Purifier experiment programmed to mimic. the cyclical continuous adsorption sequence as outlined in FIG. 1.

[0023] FIG. 4 tabulates the experimental results from an Akta Purifier experiment programmed to mimic the cyclical continuous adsorption sequence as outlined in FIG. 2.

DETAILED DESCRIPTION

[0024] Before the present embodiments are described, it is to be understood that the present disclosure is not limited to the particular apparatus, adsorbents, zones, methodologies or protocols described, as these may vary. It is also to be understood that the terminology used in the description is for the purpose of describing the particular versions or embodiments only, and is not intended to limit the scope of the present disclosure.

[0025] In general, this document provides, according to certain embodiments, for a continuous ion exchange unit operation, divided into a number of operating zones, producing a multivalent product for further purification. Such multivalent products include, but are not limited to; amino acids such as L-arginine; dicarboxylic acids such as, succinic acid, glutaric acid, adipic acid, pimelic acid and diamines such as putrescine, cadaverine, hexamethylenediamine and heptamethylenediamine, all of which are referred to as multivalent products herein. As used herein, the term divalent is used to denote a charged specie having either a 2+ or 2 valence. The term monovalent is used herein to denote a charged specie having either a 1+ or 1 valence. The term first equivalence point is used herein to denote the multivalent product's species distribution at pH=0.5.Math.(pK.sub.a1+pK.sub.a2), where pK.sub.a1 and pK.sub.a2 are the first two acid dissociation constants for the multivalent product.

[0026] As used herein, the terms unclarified refers to a solution containing solid particulates such as cells or precipitates and clarified solutions are understood to mean a solution from which solid particulates have been removed.

[0027] As used herein, adsorption zone is understood to mean a stage in the recovery method comprising at least one column where the process stream containing the multivalent product to be recovered is added to a particular adsorbent resin and adsorbs to the adsorbent resin.

[0028] Elution zone, as used herein, is understood to mean a stage in the recovery method where the multivalent product adsorbed to the adsorbent resin is desorbed into the liquid phase.

[0029] As used herein, monovalent strip zone is understood to mean a stage in the recovery method, where monovalent by-products are desorbed from the adsorbent and the valence of the multivalent product is changed from divalent to monovalent. The term monovalent adsorption zone is understood to mean a stage in the recovery method comprising at least one column where the majority of multivalent product absorbed is the monovalent specie.

[0030] The terms about and approximately when used in connection with a specific value, means that acceptable deviations from that value are also encompassed but still provide substantially the same function as the specific value.

Selective Adsorption and Particulate Removal

[0031] A clarified or unclarified aqueous solution is pH adjusted to approximately the pK.sub.a1 for cationic divalent products and to approximately the pk.sub.a2 for anionic divalent products and fed to the Adsorption Zone (see e.g., STREAM 4, FIG. 1), fed counter-current to the flow of the adsorbent phase.

[0032] The flow-through from the Adsorption Zone (see e.g., STREAM 3, FIG. 1) is combined with the flow-through from the Adsorption Wash Zone (see e.g., STREAM 5, FIG. 1) into an adsorption hold-up vessel, subsequently fed to the Dilute Adsorption Zone (see STREAM 2, FIG. 1). The Adsorption Zone and Dilute Adsorption Zone facilitate adsorption of the multivalent product in principally the divalent state onto the adsorbent phase, competing for adsorption sites with other charged inorganic and organic species in the aqueous medium. The adsorbent flow rate is set to allows for minimal or zero break-through of the multivalent product into the adsorption effluent (see e.g., STREAM 1, FIG. 1), whilst allowing for flow through of inorganic and organic charged and uncharged/zero valence species to waste treatment.

[0033] The adsorbent and interstitial hold-up in the Adsorption Zone (see e.g., COL POS: 13, FIG. 1) moves into the Adsorption Wash Zone. Water fed into the Adsorption Wash Zone (see e.g., COL POS: 15, FIG. 1) flushes the interstitial hold-up from the Adsorption Zone into the adsorption hold-up vessel, ensuring that no multivalent product, held interstitially, is carried forward into the Back wash Zone.

[0034] The Back-wash Zone fluidises the resin beds (see e.g.., COL POS: 16 & 17), providing for entrained particulate removal from the resin beds (see e.g., STREAM 6, FIG. 1).

Increasing Purity and Concentration of Adsorbed Multivalent Product Using a Separate Monovalent Strip Zone and a Separate Monovalent Adsorption Zone

[0035] The adsorbed multivalent product moves from the Back-wash Zone (see e.g., COL POS: 17, FIG. 1) into the Monovalent Strip Zone (cee e.g., COL POS: 18, FIG. 1). An air drain (see e.g., COL POS: 18, FIG. 1), recovers the interstitial water holdup carried forward from the Back-wash Zone into the monovalent strip hold-up vessel (see e.g., STREAM 7, FIG. 1).

[0036] The monovalent strip bold-up vessel is charged with a base such as NH.sub.3(g) or an acid such as HCl or H.sub.2SO.sub.4 at a concentration that allows for the effluent pH from the Monovalent Strip Zone (see e.g., STREAM 8, FIG. 1) to be approximately the pK.sub.a2 for cationic divalent products and approximately the pK.sub.a1 for anionic divalent products. The Monovalent Strip Zone is fed from the Monovalent strip hold-up vessel (see e.g., STREAM 9, FIG. 1), desorbing adsorbed species that are uncharged or having zero valence between the pH of the monovalent strip hold-up vessel and the first equivalence point. Consequently, the multivalent product is converted from the principally divalent to the largely monovalent state, freeing adsorption sites for use in the Monovalent Adsorption Zone. The flow through from the Monovalent Strip Zone is diverted to waste water treatment (see e.g. STREAM 8, FIG. 1).

[0037] Ammonia/ammonium carbonate steam stripping (see FIG. 1) to approximately the first equivalence point, produces a multivalent product that has a principally monovalent valence species distribution. The Monovalent Adsorption Zone is fed from the ammonia/ammonium carbonate stripper (see e.g., STREAM 11, FIG. 1), providing for adsorption of the monovalent specie of the multivalent product onto the free adsorbent sites, thereby increasing the concentration of the multivalent product adsorbed to the adsorbent phase. The Monovalent Adsorption Zone feed rate is set to allow for minimal or zero break-through of the multivalent product into the flow through (see e.g. STREAM 10, FIG. 1). The flow through (see e.g., STREAM 10, FIG. 1) from the Monovalent Adsorption Zone is recovered into the monovalent strip holdup vessel.

[0038] The adsorbed monovalent specie of the multivalent product moves from the Monovalent Adsorption Zone (see e.g., COL POS: 24, FIG. 1) into the Elution Zone (see COL POS: 25, FIG. 1). The Elution Zone is fed from a high concentration ammonia/ammonium hold-up vessel (see e.g., STREAM 14, FIG. 1), eluting all multivalent product from the adsorbent. The eluate (see e.g., STREAM 13, FIG. 1) is fed to the ammonia/ammonium carbonate stripper, recovering free ammonia and carbon dioxide as feed to the concentration ammonia/ammonium hold-up vessel (see e.g., STREAM 17, FIG. 1).

[0039] The regenerated resin moves from the Elution Zone (see e.g., COL POS: 27, FIG. 1) into the Elution Wash Zone (see e.g., COL POS: 28, FIG. 1). An aqueous solution, for example, water, is fed into the Elution Wash Zone (see e.g., COL POS: 29, FIG. 1) and flushes interstitial ammonia/ammonium (bi)carbonate into the concentrated ammonia/ammonium hold-up vessel (See e.g. STREAM 15, FIG. 1). Finally, the interstitial water is recovered via an air drain (see e.g., COL POS: 30, FIG. 1) into the concentrated ammonia/ammonium hold-up (see e.g., STREAM 16, FIG. 1).

[0040] The adsorbent moves from the Elution Wash Zone (see e.g., COL POS: 30, FIG. 1) into the Dilute Adsorption Zone (see e.g., COL POS: 1, FIG. 1) and the adsorbent repeats the passage through the various carousel zones as described above.

[0041] STREAM 12 (see FIG. 1) represents the net flow of multivalent product to further down-stream processing.

Increasing Purity and Concentration of adsorbed Multivalent Product Using a Combined Monovalent Strip Zone and Monovalent Adsorption Zone

[0042] The adsorbed multivalent product moves from the Back-wash Zone (see e.g., COL POS: 17, FIG. 2) into the combined Monovalent Strip and Adsorption Zone (see e.g. COL POS: 18, FIG. 2). An air drain (see e.g., COL POS: 18, FIG. 2), recovers the interstitial water hold-up carried forward from the Back-wash Zone into a water recovery hold-up vessel (see e.g., STREAM 7, FIG. 2).

[0043] Ammonia/ammonium carbonate steam stripping (see FIG. 2) to a pH where the multivalent product has a principally zero valence species distribution is fed to the combined Monovalent Strip and Adsorption Zone (see e.g., STREAM 9, FIG. 2), desorbing adsorbed species that are uncharged or having zero valence between the feed (see e.g., STREAM 9, FIG. 2) and effluent pH (see e.g., STREAM 8, FIG. 2). Consequently, the multivalent product adsorbed to the adsorbent is converted from the principally divalent to the largely monovalent state, freeing adsorption sites. Also, the zero valence multivalent product in the feed (see e.g., STREAM 9, FIG. 2) is converted to the monovalent state and adsorbed onto the free adsorbent sites, thereby increasing the concentration of the multivalent product adsorbed to the adsorbent phase. The combined Monovalent Strip and Adsorption Zone feed rate is set to allow for minimal or zero break-through of the multivalent product into the flow through (see e.g., STREAM 8, FIG. 2). The flow through (see e.g., STREAM 8, FIG. 2) from the Monovalent Adsorption Zone is diverted to waste water treatment.

[0044] The adsorbed monovalent specie of the multivalent product moves from the combined Monovalent Strip and Adsorption Zone (see e.g., COL POS: 22, FIG. 2) into the Elution Zone (see e.g., COL POS: 23, FIG. 2). The Elution Zone is fed from a high concentration ammonia/ammonium hold-up vessel (see e.g., STREAM 12, FIG. 2), eluting all multivalent product from the adsorbent. The eluate (see e.g., STREAM 10, FIG. 2) is fed to the ammonia ammonium carbonate stripper, recovering free ammonia and carbon dioxide as feed to the concentration ammonia/ammonium hold-up vessel (see e.g., STREAM 15, FIG. 2).

[0045] The regenerated resin moves from the Elution Zone (see e.g., COL POS: 27, FIG. 2) into the Elution Wash Zone (see e.g., COL POS: 28, FIG. 2). An aqueous solution, for example, water, is fed into the Elution Wash Zone (see e.g., COL POS: 29, FIG. 2) and flushes interstitial ammonia/ammonium (bi)carbonate into the concentrated ammonia ammonium hold-up vessel (see e.g. STREAM 13, FIG. 2). Finally, the interstitial water is recovered via an air drain (see e.g., COL POS: 30, FIG. 2) into the concentrated ammonia/ammonium hold-up (see e.g., STREAM 14, FIG. 2).

[0046] The adsorbent moves from the Elution Wash Zone (see e.g., COL POS: 30, FIG. 2) into the Dilute Adsorption Zone (see e.g., COL. POS: 1, FIG. 2) and the adsorbent repeats the passage through the various carousel zones as described above. STREAM 11 (see FIG. 1) represents the net flow of multivalent product to further down-stream processing.

EXAMPLES

Example 1

Recovery of Hexamethylenediamine from a Synthetic Feed Representing Clarified Fermentation Broth Using Continuous Ion Exchange with Separate Monovalent Strip and Separate Monovalent Adsorption Zone

[0047] A column with a diameter of 25.4 [mm] was packed to a flee settled bed height of approximately 600 [mm] using virgin Dowex Monosphere 650 C cationic exchange resin. The virgin resin was washed with purified water to remove solvents associated with its manufacture and converted to the NH.sub.4.sup.+ form using 10 [%] (w/w) NH.sub.3(aq) and stored in purified water.

[0048] An Akta Purifier was programmed to mimic the cyclical continuous adsorption sequence as contained in FIG. 1 for the purification of hexamethylenediamine (HMD) from a synthetic feed representing clarified fermentation broth. Accordingly, a synthetic solution having the feed purity as outlined in FIG. 3 was prepared as feed to the simulated. Adsorption Zone, having an HMD concentration of approximately 35 [g/L]. The feed to the simulated Adsorption Wash Zone was comprised of purified water. The simulated Monovalent Strip Zone feed comprised a 1 [%] (w/w) NH.sub.3(aq) solution. The feed from the ammonia/ammonium carbonate stripper to the simulated Monovalent Adsorption Zone comprised a HMD solution buffered with ammonium bicarbonate to pH=10.5 [], having a final concentration of approximately 35 [g/L]. The simulated Elution Zone feed contained 2 [M] ammonium carbonate. The simulated Elution Wash Zone feed was comprised of purified water. Each Zone was fed with 3 bed volumes at a constant flow rate of 5 [mL/min].

[0049] FIG. 3 tabulates the results from the simulated cyclical continuous adsorption experiment. FIG. 3 demonstrates that the purity of the HMD was increased from 77.4 [%] (w/w) in the feed to 99.2 [%] (w/w) in the eluate, the sequence having effectively rejected the four feed impurities down to trace quantities of lysine and glutamate. Also, the Monovalent Adsorption Zone concentrated the HMD product by a factor of 1.36. The results in FIG. 3 demonstrate that the continuous adsorption sequence outlined in FIG. 1 both purities and concentrates the desired product.

Example 2

Recovery of Hexamethylenediamine from a Synthetic Feed Representing Clarified Fermentation Broth Using Continuous Ion Exchange with a Combined Monovalent Strip and Monovalent Adsorption Zone

[0050] A column with a diameter of 25.4 [mm] was packed to a free settled bed height of approximately 600 [mm] using virgin Dowex Monosphere 650 C cationic exchange resin. The virgin resin was washed with purified water to remove solvents associated with its manufacture and converted to the NH.sub.4.sup.+ form using 10 [%] (w/w) NH.sub.3(aq) and stored in purified water.

[0051] An Akta Purifier was programmed to mimic the cyclical continuous adsorption sequence as contained in FIG. 2 for the purification of hexamethylenediamine (HMD) from a synthetic feed representing clarified fermentation broth. Accordingly, a synthetic solution having the feed purity as outlined in FIG. 4 was prepared as feed to the simulated Adsorption Zone, having an HMD concentration of approximately 54 [g/L]. The feed to the simulated Adsorption Wash Zone was comprised of purified water. The simulated combined Monovalent Strip and Adsorption Zone feed comprised a HMD solution in water, having a final concentration of approximately 54 [g/L]. The simulated Elution Zone feed contained 2 [M] ammonium carbonate. The simulated Elution Wash Zone feed was comprised of purified water. Each Zone was fed with 3 bed volumes at a constant flow rate of 5 [mL/min], barring the combined Monovalent Strip and Adsorption Zone which was fed with 2 bed volumes at a constant flow rate of 5 [mL/min].

[0052] FIG. 4 tabulates the results from the simulated cyclical continuous adsorption experiment. FIG. 4 demonstrates that the purity of the HMD was increased from 86 [%] (w/w) in the feed to 99.6 [%](w/w) in the eluate, the sequence having effectively rejected the four feed impurities down to trace quantities of lysine. Also, the combined Monovalent Strip and Adsorption Zone concentrated the HMD product by a factor of 1.38. The results in FIG. 4 demonstrate that the continuous adsorption sequence outlined in FIG. 2 both purifies and concentrates the desired product.