• 专利附录
  • 专利说明
  • 权利要求
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  • 优先权
    • 专利摘要:
    A method of removing mercury from a fluid stream comprising contacting the fluid stream with a sorbent comprising cupric sulfide. The cupric sulfide is formed from direct sulfidation of copper carbonate, without thermal decomposition of the copper carbonate to an oxide, at a temperature less than 150°C.
    公开号:AU2013217733A1
    申请号:U2013217733
    申请日:2013-01-15
    公开日:2014-07-31
    发明作者:Vladislav Ivanov Kanazirev；Dante SIMONETTI；Thomas Traynor
    申请人:UOP LLC；
    IPC主号:B01D53-02
    专利说明:
    WO 2013/119357 PCT/US2013/021510 METHOD OF REMOVING MERCURY FROM A FLUID STREAM USING HIGH CAPACITY COPPER ADSORBENTS PRIORITY CLAIM OF EARLIER NATIONAL APPLICATION [00011 This application claims priority to U.S. Application No. 13/367,219 filed 5 February 6, 2012. FIELD OF THE INVENTION [0002] The disclosure relates in general to the removal of contaminants from hydrocarbon liquids and gases. In certain embodiments, the disclosure relates to the use of a copper-based sorbent to remove mercury from hydrocarbon streams. In certain embodiments, 10 the disclosure relates to the use of a high capacity sorbent comprising a copper sulfide compound, where the copper sulfide compound was produced by way of direct sulfidation of a copper oxysalt. BACKGROUND OF THE INVENTION [00031 Hydrocarbon fluid streams, including both liquid and gas streams, are often 15 contaminated with mercury compounds. Sorbents containing supported metal sulfides, such as copper sulfide (CuS), have been used to scavenge mercury from hydrocarbon fluid streams by reaction 1. 2CuS + Hg - HgS + Cu 2 S (1) [0004] For example, U.S. Pat. No. 4,094,777 describes a solid mass that contains a carrier 20 and sulfided copper as an absorbent for mercury from a gas or a liquid. CuS based materials for Hg removal are offered by Axens, Johnson Matthey and others for applications in the natural gas and hydrocarbon industries. [0005] Prior art methods of producing copper sulfide sorbents include a two-step process. A copper carbonate is first decomposed to cupric oxide and the cupric oxide is subsequently 25 sulfided to produce the active copper sulfide component of the sorbent. The decomposition of copper carbonate and the sulfidation of copper oxide requires relatively high temperatures, resulting in the agglomeration or clumping of the active component of the sorbent. The reduction of surface area limits the utilization of the active component. High utilization of the - 1 - WO 2013/119357 PCT/US2013/021510 active copper sulfide component is desirable to decrease adsorbent bed volume and/or increase the adsorbent service lifetime. Accordingly, there is a need for higher capacity mercury sorbents that (i) are capable of scavenging more mercury per quantity of active component and/or (ii) have higher levels of active component utilization than prior art 5 compositions and methods. SUMMARY OF THE INVENTION [0006] A method of removing mercury from a fluid stream is presented. The method comprises contacting the fluid stream with a sorbent comprising cupric sulfide. The cupric sulfide is formed from direct sulfidation of copper carbonate, without thermal decomposition 10 of the copper carbonate to an oxide, at a temperature of less than 150'C. BRIEF DESCRIPTION OF THE DRAWINGS [0007] FIG. 1 is a graph of breakthrough curves for a prior art adsorbent and one embodiment of Applicants' sorbent, each having a 7x14 mesh size; and [00081 FIG. 2 is a graph of breakthrough curves for a prior art absorbent and one 15 embodiment of Applicants' sorbent, each having a 5x8 mesh size. DETAILED DESCRIPTION OF PREFERRED EMBODIMENTS [0009] The invention is described in preferred embodiments in the following description with reference to the Figures, in which like numerals represent the same or similar elements. Reference throughout this specification to "one embodiment," "an embodiment," or similar 20 language means that a particular feature, structure, or characteristic described in connection with the embodiment is included in at least one embodiment of the present invention. Thus, appearances of the phrases "in one embodiment," "in an embodiment," and similar language throughout this specification may, but do not necessarily, all refer to the same embodiment. [0010] The terms sorbent, adsorbent, and absorbent as used herein refer to the ability of a 25 material to take in or soak up liquid or gas components on the surface thereof or to assimilate such components into the body thereof. [0011] Methods of producing copper-based sorbents, and sorbents produced by such methods, are presented. In one embodiment, Applicants' sorbent comprises a copper material disposed within a support material. In various embodiments, the sorbent comprises a copper -2- WO 2013/119357 PCT/US2013/021510 sulfide disposed within a support material. In various embodiments, the copper sulfide is cupric sulfide (CuS). In various embodiments, the copper sulfide is cuprous sulfide (Cu2S). [0012] In various embodiments, the support material is a metal oxide selected from the group consisting of alumina, silica, silica-aluminas, silicates, aluminates, silico-aluminates 5 such as zeolites, titania, zirconia, hematite, ceria, magnesium oxide, and tungsten oxide. In one embodiment, the support material is alumina. In some embodiments, the support material is carbon or activated carbon. In certain embodiments, Applicants' sorbent does not comprise a binder. [0013] In various embodiments, the alumina support material is present in the form of 10 transition alumina, which comprises a mixture of poorly crystalline alumina phases such as "rho," "chi" and "pseudo gamma" aluminas which are capable of quick rehydration and can retain substantial amounts of water in a reactive form. An aluminum hydroxide Al(OH) 3 , such as gibbsite, is a source for preparation of transition alumina. The prior art industrial process for production of transition alumina includes milling gibbsite to 1-20 microns particle 15 size followed by flash calcination for a short contact time as described in the patent literature such as in U.S. Pat. No. 2,915,365. Amorphous aluminum hydroxide and other naturally found mineral crystalline hydroxides e.g., Bayerite and Nordstrandite or monoxide hydroxides, AlOOH, such as Boehmite and Diaspore can be also used as a source of transition alumina. In certain embodiments, the BET surface area of this transition alumina 20 material is 300 m 2 /g and the average pore diameter is 45 angstroms as determined by nitrogen adsorption, resulting in a porous sorbent. 100141 In various embodiments, a solid oxysalt of a transition metal is used as a starting component of the sorbent. "Oxysalt," by definition, refers to any salt of an oxyacid. Sometimes this definition is broadened to "a salt containing oxygen as well as a given anion." 25 FeOCl, for example, is regarded as an oxysalt according this definition. [0015] In certain embodiments, the oxysalt comprises one or more copper carbonates. In certain embodiments, the oxysalt comprises one or more basic copper carbonates. Basic copper carbonates, such as Cu2(O-I)2CO3, can be produced by precipitation of copper salts, such as Cu(NO) 3 , CuSO 4 and CuCl 2 , with sodium carbonate. In one embodiment, a synthetic 30 form of malachite, a basic copper carbonate, produced by Phibro Tech, Ridgefield Park, N.J., is used as a component of the sorbent. -3- WO 2013/119357 PCT/US2013/021510 [00161 Depending on the conditions used, and especially on washing the resulting precipitate, the final material may contain some residual product from the precipitation process. In the case of the CuCl 2 raw material, sodium chloride is a side product of the precipitation process. It has been determined that a commercially available basic copper 5 carbonate that had both residual chloride and sodium exhibited lower stability towards heating and improved resistance towards reduction than other commercial basic copper carbonates that were practically chloride-free. 100171 In one embodiment, the particle size of the green sorbent beads (i.e., the basic copper carbonate particles) is in the range of that of the transition alumina, namely 1-20 10 microns. In other embodiments, the green sorbent bead comprises the oxysalt Azurite, Cu 3
    (OH)
    2
    (CO
    3
    )
    2 . In other embodiments, the green sorbent bead comprises an oxysalt of copper, nickel, iron, manganese, cobalt, zinc or a mixture thereof. 100181 In certain embodiments, the green sorbent bead comprises between 5 mass percent to 85 mass percent copper, calculated as CuO on a volatile-free basis. In one embodiment, the 15 green sorbent bead comprises 70 mass percent copper. [0019] The sorbent is produced by exposing the green sorbent bead to a sulfiding environment. In various embodiment, the sulfiding environment comprises hydrogen sulfide
    (H
    2 S), other organic or inorganic substances capable of releasing H 2 S under thermal treatment, such as without limitation dimethyl disulfide or polysulfides, or a combination 20 thereof In one embodiment, the green sorbent bead is sulfided at temperatures less than 150 0 C. In one embodiment, the green sorbent bead is sulfided at temperatures between 100 0 C and 150 0 C. The copper carbonate is directly sulfided without formation of a copper oxide intermediate. In certain embodiments, after the sulfiding step, the resulting sorbent comprises no residual copper carbonate. In certain embodiments, after the sulfiding step, the resulting 25 sorbent comprises no copper oxide. [00201 In certain embodiments, the sorbent comprises 10 mass percent to 80 mass percent copper sulfide. In certain embodiments, the sorbent comprises 5 mass percent to 23 mass percent sulfur in the form of copper sulfide. In certain embodiments, the sorbent comprises 12 mass percent to 18 mass percent sulfur in the form of copper sulfide. In certain 30 embodiments, the sorbent comprises 14 mass percent sulfur in the form of copper sulfide. [00211 In certain embodiments, the final sorbent beads have a diameter (for spherical beads) or maximum width (for irregular shaped beads) of 1 mm to 10 mm. In certain -4- WO 2013/119357 PCT/US2013/021510 embodiments, the final sorbent beads have a diameter or maximum width of 1.2 mm to 5 mm. [0022] In various embodiments, the final sorbent beads are porous (i.e., have a plurality of pores and voids extending therethrough). In certain embodiments, the pore volume of the 5 final sorbent beads is at least 0.12 cm 3 /g. In various embodiments, the final sorbent beads have a bulk density of between 640 kg/m 3 (40 lbs/ft 3 ) to 1280 kg/m 3 (80 lbs/ft). In various embodiments, the final sorbent beads have a bulk density of 880 kg/m 3 (55 lbs/ft 3 ) to 1150 kg/m 3 (72 lbs/ft). [0023] In various embodiments, the final sorbent beads are disposed within a flow reactor 10 configuration and exposed to a hydrocarbon fluid (i.e., gas or liquid) stream. In various embodiments, the fluid stream comprises between 0.1 parts per billion (ppb) to 1000 ppb mercury. 100241 The crystal size of the copper sulfide formed by one embodiment of Applicants' method as compared to crystals produced by prior art methods is set forth in Table 1 below. 15 The crystal size is determined using X-ray powder diffraction (XRD) and the Scherrer equation (1), where K is the shape factor, k is the x-ray wavelength, f is the line broadening at half the maximum peak intensity (FWHM) in radians, 0 is the Bragg angle, and -C is the mean size of the crystalline domains, which may be smaller or equal to the grain size. KA 20 Table 1 AdsorbentType Dimension at 27.2020 Dimension at 32.9020 (1,0,0) in A (0,0,6) in A Prior Art CuS Adsorbent 287 166 New CuS Adsorbent Produced 278 79 by Applicants' Method [0025] The first row of Table 1 represents 7x14 mesh beads of a prior art adsorbent produced by a two-step process where copper carbonate is first decomposed to a copper oxide and the copper oxide sulfided to a copper sulfide. The prior art absorbent has 37 mass percent CuS. -5- WO 2013/119357 PCT/US2013/021510 [00261 The second row of Table I represents 7x14 mesh beads produced by one embodiment of Applicants' method of direct sulfidation of a basic copper carbonate and having 75 mass percent CuS. The crystallite dimensions across vector (0,0,6) in Table I for adsorbents produced by Applicants' method are less than 50% of the corresponding 5 dimensions for the prior art sample. The dimensions are presented in angstroms. Smaller crystallite dimensions result in greater surface area available for mercury scavenging and, therefore, higher adsorbent performance. In one embodiment, the crystallite size of the cupric sulfide measured on a (0,0,6) plane is less than 100 angstroms. In one embodiment, the crystallite size of the cupric sulfide measured on a (0,0,6) plane is less than 80 angstroms. 10 [00271 Referring to FIG. 1, a graph comparing the breakthrough curve of a prior art adsorbent against one embodiment of Applicants' adsorbent is presented. The x-axis represents the loading of the adsorbent in a test chamber in grams of mercury to grams of sulfur (g Hg/g S). The y-axis represents the concentration of mercury at the outlet of the test chamber in micrograms of mercury per cubic meter ( g/m 3 ). 15 [00281 Curve 102 represents a prior art adsorbent with a 7x14 mesh size (beads having a minimum dimension of smaller than 1.2 mm and greater than 2.8 mm). Below a loading of 0.07 g Hg/g S, the prior art sorbent adsorbed all mercury, as indicated by the absence of mercury at the test chamber outlet. Above a loading of 0.07 g Hg/g S, the prior art sorbent was unable to adsorb the mercury flowing through the test chamber, as indicated by the 20 presence of mercury at the outlet. The amount of mercury measured at the outlet continued to increase as the mercury loading of the adsorbent beads increased. 100291 Curve 104 represents Applicants' high-capacity sorbent beads with a 7x14 mesh size. Applicants' high-capacity sorbent beads were able to fully absorb mercury within the test chamber, up to a loading greater than 0.35 g Hg/g S, where a very small amount of 25 mercury was detected at the outlet. [0030] Referring to FIG. 2, a graph comparing the breakthrough curve of a prior art adsorbent against another embodiment of Applicants' adsorbent is presented. The x-axis represents the loading of the adsorbent in a test chamber in grams of mercury to grams of sulfur (g Hg/g S). The y-axis represents the concentration of mercury at the outlet of the test 30 chamber in micrograms of mercury per cubic meter ( g/m 3 ). 100311 Curve 202 represents a prior art adsorbent with a 5x8 mesh size (beads having a minimum dimension of smaller than 4.0 mm and greater than 2.4 mm). Below a loading of -6- WO 2013/119357 PCT/US2013/021510 0.04 g I-g/g S, the prior art sorbent adsorbed all mercury, as indicated by the absence of mercury at the outlet. Above a loading of 0.04 g Hg/g S, the prior art sorbent was unable to adsorb the mercury flowing through the test chamber, as indicated by the presence of mercury at the outlet. Curve 202 increases linearly at a first slope above a loading of 0.04 g 5 Hg/g S. [00321 Curve 204 represents Applicants' high-capacity sorbent beads with a 5x8 mesh size. Applicants' high-capacity sorbent beads were able to fully absorb mercury within the test chamber, up to a loading of 0.09 g Hg/g S. Above a loading of 0.09 g Hg/g S, curve 204 increases linearly at a second slope, where the first slope is at least two times the second 10 slope. [00331 The following Example is presented to further illustrate to persons skilled in the art how to make and use the invention. This Example is not intended as a limitation, however, upon the scope of Applicant's invention. EXAMPLE 15 100341 A mixture of a copper oxysalt and a support material is provided. In one embodiment, the copper oxysalt is basic copper carbonate, Cu 2
    (OH)
    2
    CO
    3 and the support material is alumina powder capable of rehydration. In different embodiments, the copper content of the mixture, calculated as CuO on a volatile-free basis, is between 5 mass percent and 85 mass percent. In one embodiment, the copper content of the mixture is 70 mass 20 percent. [00351 Green sorbent beads are formed from the mixture. As used herein, "green sorbent beads" refer to beads containing the copper oxysalt before any sulfidation and "activated sorbet beads" refer to beads where at least a portion of the copper oxysalt has been sulfided. In one embodiment, the beads are formed by nodulizing the mixture in a rotating pan 25 nodulizer while spraying with a liquid. In one embodiment, the liquid comprises water. In one embodiment, the liquid comprises a solution of water and a halide salt. In one embodiment, the halide salt is sodium chloride. In one embodiment, the solution comprises an I mass percent to 3 mass percent solution of sodium chloride. [0036] In another embodiment, the green sorbent beads are formed by agglomeration. In 30 another embodiment, the green sorbent beads are formed by extrusion. Those skilled in the art will appreciate that other methods may be performed to produce regular- or irregular -7- WO 2013/119357 PCT/US2013/021510 shaped beads, with or without a halide salt, that fall within the scope of Applicants' invention. [0037] The green sorbent beads are cured and dried. In one embodiment, the curing occurs at 60'C. In one embodiment, the beads are dried in a moving bed activator at 5 temperatures at or below 175 0 C. In one embodiment, the activated sorbent beads comprise 0.5 mass percent to 0.8 mass percent chloride. [00381 The green sorbent beads are activated by exposure to a sulfiding environment. As would be appreciated by those skilled in the art, the length of exposure, the composition of the sulfiding environment, and temperature are selected based on the desired composition of 10 the active copper components in the final sorbet product. In certain embodiments, the sulfiding environment comprises hydrogen sulfide (H 2 S). In various embodiments, the sulfiding environment comprises between 0.0005 mole percent and 100 mole percent hydrogen sulfide (H 2 S), the balance being an inert gas. [00391 In one embodiment, the sulfidation occurs at between 100 C to 150'C. In certain 15 embodiments, the copper in the green material is fully sulfided. In one embodiment, the activated sorbent comprise 37 mass percent CuS. In certain embodiments, the activated sorbent comprises between 10 mass percent to 80 mass percent CuS. The activated beads are then exposed to a hydrocarbon fluid stream containing sulfur- and/or mercury-containing materials. 20 [00401 The described features, structures, or characteristics of the invention may be combined in any suitable manner in one or more embodiments. In the above description, numerous specific details are recited to provide a thorough understanding of embodiments of the invention. One skilled in the relevant art will recognize, however, that the invention may be practiced without one or more of the specific details, or with other methods, components, 25 materials, and so forth. In other instances, well-known structures, materials, or operations are not shown or described in detail to avoid obscuring aspects of the invention. In other words, the present invention may be embodied in other specific forms without departing from its spirit or essential characteristics. The described implementations are to be considered in all respects only as illustrative and not restrictive. The scope of the invention should, therefore, 30 be determined not with reference to the above description, but instead should be determined with reference to the pending claims along with their full scope or equivalents, and all -8- WO 2013/119357 PCT/US2013/021510 changes which come within the meaning and range of equivalency of the claims are to be embraced within their full scope. -9-
    权利要求:
    Claims (10)
    [1] 1. A method of removing mercury from a fluid stream, comprising contacting said fluid stream with a sorbent comprising cupric sulfide, wherein said cupric sulfide is formed from direct sulfidation of copper carbonate, without thermal decomposition of the copper 5 carbonate to an oxide, at a temperature less than 150'C.
    [2] 2. The method of claim 1, wherein the sorbent comprises no residual copper carbonate.
    [3] 3. The method of claim 2, wherein said sorbent comprises no copper oxide.
    [4] 4. The method of claim 1, wherein said sorbent does not comprise a binder. 10
    [5] 5. The method of claim 1, wherein said copper carbonate is Cu 2 (OH) 2 CO 3 .
    [6] 6. The method of claim 1, wherein said metal oxide is selected from the group consisting of alumina, silica, silica-aluminas, silicates, aluminates, silico-aluminates, zeolites, titania, zirconia, hematite, ceria, magnesium oxide, and tungsten oxide.
    [7] 7. The method of claim 6, wherein said sorbent comprises 5 mass percent to 23 mass 15 percent sulfur in the form of cupric sulfide.
    [8] 8. The method of claim 1, wherein said sulfiding environment has a H 2 S concentration of between 0.0005 mole percent to 100 mole percent.
    [9] 9. The method of claim 1, wherein a crystallite size of said cupric sulfide measured on a (0,0,6) plane is less than 100 angstroms. 20 10. The method of claim 1, wherein the bulk density of said sorbent is between 640 kg/m 3 (40 lbs/ft 3 ) to 1280 kg/m 3 (80 lbs/ft).
    [10] - 10 -
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    法律状态:
    2016-02-25| FGA| Letters patent sealed or granted (standard patent)|
    优先权:
    申请号 | 申请日 | 专利标题
    US13/367,219|US8876952B2|2012-02-06|2012-02-06|Method of removing mercury from a fluid stream using high capacity copper adsorbents|
    US13/367,219||2012-02-06||
    PCT/US2013/021510|WO2013119357A1|2012-02-06|2013-01-15|Method of removing mercury from a fluid stream using high capacity copper adsorbents|
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