Classifications

• • B—PERFORMING OPERATIONS; TRANSPORTING
  • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
  • B01D—SEPARATION
  • B01D47/00—Separating dispersed particles from gases, air or vapours by liquid as separating agent
  • B01D47/02—Separating dispersed particles from gases, air or vapours by liquid as separating agent by passing the gas or air or vapour over or through a liquid bath
• • B—PERFORMING OPERATIONS; TRANSPORTING
  • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
  • B01D—SEPARATION
  • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
  • B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
  • B01D53/1493—Selection of liquid materials for use as absorbents
• • B—PERFORMING OPERATIONS; TRANSPORTING
  • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
  • B01D—SEPARATION
  • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
  • B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
  • B01D53/1418—Recovery of products
• • B—PERFORMING OPERATIONS; TRANSPORTING
  • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
  • B01D—SEPARATION
  • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
  • B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
  • B01D53/1456—Removing acid components
  • B01D53/1468—Removing hydrogen sulfide
• • B—PERFORMING OPERATIONS; TRANSPORTING
  • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
  • B01D—SEPARATION
  • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
  • B01D53/34—Chemical or biological purification of waste gases
  • B01D53/46—Removing components of defined structure
  • B01D53/48—Sulfur compounds
  • B01D53/52—Hydrogen sulfide
• • C—CHEMISTRY; METALLURGY
  • C01—INORGANIC CHEMISTRY
  • C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
  • C01B17/00—Sulfur; Compounds thereof
  • C01B17/02—Preparation of sulfur; Purification
  • C01B17/04—Preparation of sulfur; Purification from gaseous sulfur compounds including gaseous sulfides
  • C01B17/05—Preparation of sulfur; Purification from gaseous sulfur compounds including gaseous sulfides by wet processes

Definitions

• This invention relates to compositions, processes and apparatus for removing hydrogen sulfide from gases using polyvalent metal chelate catalysts in aqueous solution.
• Patent 4,525,338 to Klee U.S. Patent 4,532,118 to Nagiri et al.
• U.S. Patent 4,534,955 to Rosenbaum U.S. Patent 4,649,032 to Snavely et al.
• Shell Redox Desulfurization Process Stresses Versatility by Fong et al.. Oil and Gas Journal (OGJ Report), May 25, 1987, pp. 54-62.
• the hydrogen sulfide removal processes using aqueous solutions of polyval ⁇ ent metal chelate catalyst include various multi- 5 stage processes for (a) oxidizing hydrogen sulfide to elemental sulfur in a gas-liquid contacting vessel, (b) separating the sulfur from the aqueous solution by settling, frothing, filtration or other means for removing the solid elemental sulfur, (c) regenerating
• the amount of H 2 S present in gas streams varies, as can the size of the gas stream, and thus the amount of H 2 S that must be removed on a daily basis can
• H S removal 25 vary from as high as thousands of tons per day to as little as a few pounds per day.
• Another commercial process uses an aqueous solution of sodium nitrite to react with H 2 S when the sour gas is passed through a static fluid column in a single vessel.
• the nitrite is all used up, the material is discharged and discarded as Class II waste, and a fresh charge is loaded into the vessel.
• a disadvantage of this process is that the sodium nitrite chemical solution is comparatively expensive.
• Another object of this invention is to enable the removal of H 2 S in a simple process, using simple equipment that requires little operation attention and/or maintenance.
• Yet another object of this invention is to provide catalytic method for H 2 S conversion to sulfur in the presence of oxygen in a single gas/liquid contact vessel. Another object of this invention is to disperse the precipitated sulfur to very small particles to prevent settling, foaming, frothing and fouling in the gas/liquid contact zone.
• this invention provides a composition for removing hydrpgen sulfide from a gaseous stream in the presence of oxygen comprising an aqueous solution containing: a) from about 0.005 to about 0.2 percent by weight of a polyvalent metal in a chelate complex with; b) from about 0.005 to about 1 percent by weight of a chelating agent; c) up to the solubility limit of a pH buffer; d) at least about 0.001 percent of a dispersing agent for dispersing the sulfur particles present in the aqueous solution; and e) up to about 0.02 percent by weight of an anti-foaming agent.
• this invention provides a process for removing hydrogen sulfide from a gaseous stream which comprises contacting said hydrogen sulfide containing gaseous stream with an aqueous solution of a water soluble oxidized polyvalent metal chelate catalyst to convert the hydrogen sulfide to particulate elemental sulfur and reduce the polyvalent metal chelate catalyst, said contacting taking place in the presence of sufficient oxygen for oxidizing the reduced polyvalent metal chelate catalyst to its oxidized state, thereby forming a suspension of the particulate elemental sulfur in said aqueous solution, continuing said contacting until the particulate elemental sulfur reaches a predetermined percent by weight of the aqueous solution, discarding at least a portion of the aqueous solution containing the suspension of particulate elemental sulfur, and replacing the discarded aqueous solution with fresh aqueous solution of said water soluble oxidized polyvalent metal chelate catalyst for contact with additional hydrogen sulfide containing gaseous stream.
• this invention provides a process for removing hydrogen sulfide from a gaseous stream which comprises contacting said hydrogen sulfide containing gaseous stream with an aqueous solution of water soluble oxidized polyvalent metal chelate catalyst to convert the hydrogen sulfide to ' particulate elemental sulfur and reduce the polyvalent metal chelate catalyst, said contacting taking place in the presence of sufficient oxygen for oxidizing the reduced polyvalent metal chelate catalyst to its oxidized state, thereby forming a suspension of particulate elemental sulfur in said aqueous solution wherein the aqueous solution contains an effective amount of a dispersing agent for maintaining the particulate elemental sulfur in the form of dispersed particles and maintaining said sulfur particles in suspension in the aqueous solution.
• this invention provides a process for removing hydrogen sulfide from gaseous stream which comprises contacting said hydrogen sulfide containing gaseous stream with an aqueous solution of a water soluble oxidized polyvalent metal chelate catalyst to convert the hydrogen sulfide to particulate elemental sulfur and reduce the polyvalent metal chelate catalyst, said contacting taking place in the presence of sufficient oxygen for oxidizing the reduced polyvalent metal chelate catalyst to its oxidized state, thereby forming and maintaining a suspension of the particulate elemental sulfur in said aqueous solution wherein the average particle size of the particulate elemental sulfur is less than about 15 microns.
• this invention provides a process for removing hydrogen sulfide from a gaseous stream which comprises contacting in a reduction zone said hydrogen sulfide containing gaseous stream with an aqueous solution of a water soluble oxidized polyvalent metal chelate catalyst to convert the hydrogen sulfide to particulate elemental sulfur and reduce the polyvalent metal chelate catalyst, contacting a portion of the solution containing reduced polyvalent metal chelate catalyst in an oxidation zone with an oxidation containing gas sufficient for oxidizing at least a portion of the reduced catalyst to its oxidized form, wherein the reduction and oxidation zones are each adapted for allowing gas to pass upwardly through the aqueous solution contained therein, each zone has a gas in-let and a gas outlet positioned such that the respective gas streams do not mix and the zones are in communication only at the lower ends thereof to allow solution to pass between the zones, thereby forming a suspension of the particulate elemental sulfur in said aqueous solution, continuing said contacting
• Figure 1 ' shows an apparatus for the basic operation of the process of this invention.
• Figure 2 shows an exemplary embodiment of apparatus for practicing a preferred aspect of the present invention.
• the present invention provides a process for removing hydrogen sulfide from a gaseous stream by contacting the gaseous stream with an aqueous solution of a polyvalent metal chelate catalyst in a single contact/reaction zone in the presence of oxygen without the necessity of removing the elemental or precipitated sulfur from the solution. This is accomplished in its most fundamental form by keeping the precipitated elemental sulfur in a dispersed slurry or suspension in the solution and not allowing the sulfur to agglomerate, settle, foam or froth.
• the dispersed particulate elemental sulfur content of the aqueous solution can be increased to at least about 1 or 2- percent by weight of the aqueous solution, preferably about 4 or 5 percent, more preferably about 8 percent, and in many cases can be about 10 percent or greater and still be maintained in aqueous slurry or suspension form because of the dispersing agent.
• the solution reaches a desired or predetermined maximum percent by weight of dispersed and/or suspended elemental sulfur precipitate particles, preferably the entire solution is removed from the contact zone and discarded and disposed of.
• Fresh polyvalent metal chelate catalyst solution is then added to replace the discarded solution and the process resumed until the dispersed precipitated sulfur particles again reaches the desired concentra ⁇ tion in the solution and the cycle again repeated.
• the solution containing the precipitated sulfur particles can be removed in a small continuous stream and discarded, and fresh catalyst solution can be added continuously to replace the withdrawn and discarded solution.
• This variation of the process of this invention can serve to remove sufficient sulfur from the contact vessel and keep sufficient metal chelate catalyst present without shutting down the process to replace all the solution at once, while still providing the benefits of not having to operate separate sulfur separation equipment or separate catalyst regeneration equipment.
• This variation of the process can be particularly advantageous when low levels of metal chelate catalyst are sufficient for conversion of the H 2 S in the gaseous stream being treated.
• the process of this invention eliminates the • necessity of separating the precipitated sulfur from the solution which is one factor which makes the process of the present invention much more economical to operate than conventional H 2 S removal processes.
• the spent solution containing the dispersed slurry of elemental sulfur particles can be disposed of in conventional methods as a low-level contaminate, for example, by evaporation in holding ponds.
• the process comprises:
• step (g) restarting the gas flow as in step (a) .
• H 2 S is transported from the gas phase to the liquid phase by mass transfer where it dissolves in the solution that is pH buffered, preferably to a pH between 6.5 and 8.5. It is preferred to operate at a higher pH because higher pH increases the absorption rate of H 2 S and improved scrubbing is observed.
• the H 2 S then reacts with ferric ion in solution and is oxidized to elemental sulfur while the ferric ion is reduced to ferrous ion.
• the sulfur appears as small particles that remain in suspension in the liquid phase.
• the ferrous ion is reoxidized back to ferric ion by oxygen present.
• the net reaction is that of one mole H 2 S reacting with 1/2 mole oxygen to produce sulfur and water as described above.
• the single contact zone used in the process of the present invention is made possible by the presence of oxygen in the system.
• Oxygen is fre ⁇ quently present in the gaseous streams being treated.
• additional oxygen must be added to.the gaseous stream or added to the contact zone in sufficient quantity to assure the oxidation of at least a portion, preferably at least a substantial portion of the reduced polyvalent metal chelate catalyst back to its oxidized form.
• This oxidation of the reduced metal chelate catalyst by oxygen present in the solution occurs essentially simultaneously with the oxidation of the hydrogen sulfide to produce elemental sulfur by the reduction of the polyvalent metal chelate catalyst.
• a first zone may be used for contacting the hydrogen sulfide with the polyvalent metal chelate catalyst solution to oxidize the hydrogen sulfide and to reduce the catalyst and a separate or second zone used for contacting the reduced catalyst with an oxygen containing gas to oxidize the catalyst to its oxidized form.
• the gaseous streams for which the present invention is suitable for treatment and removal of hydrogen sulfide includes any conventional gaseous stream which has typically been treated for the removal of hydrogen sulfide using various aqueous solutions, particularly the solutions containing water soluble nitrite and solutions containing polyvalent metal chelate catalysts.
• the process of the present invention is particularly suited for treating gaseous streams containing low levels of hydrogen sulfides such as less .than 1000 ppm, but the process of the present invention can be used to effectively and economically to remove essentially all of the hydrogen sulfide in a gaseous stream containing 20000 ppm or more of hydrogen sulfide.
• freshness solution includes either new solution or solution from which the elemental sulfur has been removed so the solution can be reused.
• the process of the present invention is highly efficient and effective.
• a gaseous stream containing 500 ppm hydrogen sulfide can be treated in a single pass through the single contact zone of the present invention to produce a gaseous stream containing less than 4 ppm hydrogen sulfide.
• the efficiency and effectiveness of the process of the present invention will depend upon various factors, as discussed herein, which are conventionally known to affect the hydrogen sulfide oxidation to sulfur in an aqueous polyvalent metal chelate solution.
• the gaseous streams which can be treated by the process of the present invention can contain various materials and components such as carbon dioxide, nitrogen, etc.
• the gaseous stream should not contain any significant liquid hydrocarbons or other materials which may interfere with the aqueous solution of the polyvalent metal chelate catalyst.
• other components such as acid gases like carbon dioxide are present, it will be necessary to maintain the pH of the aqueous solution in the desired range by use of a conventional buffer material.
• Other components in the gaseous stream can be dealt with by one skilled in the art as conventionally recognized in the process of treating hydrogen sulfide containing gases with aqueous solutions of polyvalent metal chelate catalyst.
• the oxygen content of the gaseous stream be sufficient to provide the necessary oxygen for oxidizing the reduced polyvalent metal chelate catalyst to its oxidized form in the solution in the contact zone. If the gaseous stream does not " contain sufficient oxygen, oxygen may be added directly to the gaseous stream in the form of air or other oxygen-containing gas. Alternatively, the oxygen or ⁇ xygen-containing gas can be bubbled directly into the aqueous solution in the same general area or zone of the solution where the gaseous stream in contacting the solution.
• the oxygen or oxygen-containing gas can also be bubbled directly into the aqueous solution in a separate contacting zone whereby additional and/or excess oxygen can be contacted with the solution to oxidize the catalyst in the solution to its oxidized form, but the excess oxygen or oxygen-containing gas does not dilute or mix with the gas being treated to remove the hydrogen sulfide.
• excess oxygen or oxygen-containing gas does not dilute or mix with the gas being treated to remove the hydrogen sulfide.
• a ratio of at least about 2 moles oxygen per mole of hydrogen sulfide can be used as well as higher ratios, such as 10:1 or even 100:1.
• the present invention can provide the added benefit of the reducing oxygen in the gaseous stream being treated. This can be particularly advantageous in gaseous streams such as natural gas production from oil fields.
• the process of the present invention can simultaneously reduce the hydrogen sulfide as well as the oxygen content of the natural gas and thereby produce a gas stream suitable for sales into residential uses.
• a natural gas stream containing 2,500 ppmv oxygen and 1,000 ppmv hydrogen sulfide can be treated by the process of the present invention to produce the gas having less than 4 ppmv hydrogen sulfide and about 2,000 ppmv oxygen.
• the pH of the aqueous solution should be maintained between about 6.5 and about 8.5. While the process may be operated at pH's lower or higher than this preferred range, one skilled in the art will recognize that when the pH is at a low level, the rate of absorption of the hydrogen sulfide into the solution will decrease. Also, if the pH is allowed to increase, the likelihood that metal hydroxides will form as precipitates will be increased. It should be noted that the pH may be quite high, such as 10 or even 12, when a solution is first put into use, but will quickly drop to the desired level once operation begins. Preferably, the pH should be maintained in the range of about 7 to about 8.
• Buffering agents are normally used to maintain the pH in the desired range and compensate for any acidic or other materials which may be absorbed into the aqueous solution of the gaseous stream being treated.
• Some preferred buffering agents are alkaline earth metal bicarbonates, carbonates and hydroxides, preferably sodium bicarbonate, but other buffering agents known in the art may be used.
• the amount of the buffering agent used may be up to the solubility limit of the agent in the solution, which may be as much as 25% by weight in some cases but usually will be up to 10% or 15% by weight.
• the temperatures at which the process of the present invention perform are ambient condition temperatures but lower or higher temperatures may be used.
• the pressures at which the process of the present invention can be operated range from 1 atmosphere to 1000 psi or higher. Basically, the process of the present invention can be used at any prevailing gas stream pressures. Higher pressures usually increase the rate at which the hydrogen sulfide and oxygen will go into the solution. Since hydrogen sulfide goes into solution fairly rapidly, particularly at alkaline pH, a rate-limiting factor on the process of the present invention is the rate the oxygen will go into solution. Therefore, it is usually advantageous to have a higher oxygen partial pressure.
• the equipment useful in the process of the present invention need only comprise a single vessel for holding the polyvalent metal chelate solution and contain means for dispersing the gaseous stream in the vessel for contacting the gaseous stream with the aqueous solution, typically by bubbling the gas stream through the aqueous solution.
• the equipment is very similar to the equipment that is used in the sodium nitrite processes and the caustic scrubbing processes.
• Contact vessel 1 is a typical gas liquid contact vessel of conventional sizing such as 3 feet in diameter and 12 feet in height and which has gas inlet means 2 and sparging means 3 for dispersing the incoming gaseous stream into small bubbles and the aqueous solution 4.
• gas inlet means 2 and sparging means 3 for dispersing the incoming gaseous stream into small bubbles and the aqueous solution 4.
• the height of the vessel will be about twice the height of the aqueous solution, thus a typical height of the aqueous solution in a 15-20 foot vessel would be in the range of 8 to 10 feet.
• sour gas entering the vessel for treatment contain sufficient oxygen according to the process of the present invention
• separate air injections means 5 may be provided for adding oxygen to the incoming sour gas before the gas enters the contact vessel.
• the contact vessel is provided with a drain means 6 which can be used to empty the vessel when the solution in the vessel reaches a predetermined sulfur content, such as 5 or 10 percent by weight sulfur.
• Outlet means 6 can also be used to draw off daily amounts of the solution which may be replaced by equivalent amounts of fresh solution through inlet means 7 in order to maintain the desired level of chelate concentration in the contact vessel and to remove sulfur from the system.
• the contact vessel is also provided with a sweet gas outlet 8 and if desired, may be fitted with demisting means 9.
• the contact vessel may also be fitted with minimum level and maximum level taps 1 ' 0 and 11 for monitoring and/or controlling the level of the aqueous solution in the contact vessel. It is desirable that drain 6 and taps 10 and 11 be provided with a holding tank 12 in which the spent solution can be held until transport is available to dispose of the spent solution. Likewise, it is desirable to provide a holding tank 13 for makeup solution and providing fresh solution to the contact vessel.
• the contact vessel can also be equipped monitoring equipment to monitor pH, color of the solution, level of the solution, the presence of foaming and other conditions which may be desirable to monitor for control of the process.
• Figure 2 illustrates a different and in some cases a preferred embodiment for practicing the process of the present invention.
• FIG. 21 which is one embodiment or example of how this aspect of the process of this invention may be practiced.
• Vessel 21 contains separate zones for gas- liquid contact which are zones 22 and 23.
• gas inlet means 24 and gas outlet means 25 are provided along with solution inlet means 26 and outlet means 27.
• Gas inlet means 24 may include a separate oxygen inlet means as in Figure 1, and the other aspects or elements in Figure 1 may be used in this embodiment as well.
• zone 23 there are provided gas inlet means 31 regulated by control valve 32 and gas outlet means 33 regulated by control valve 34. Zones 22 and 23 communicate only at the bottom or lower portions thereof to allow the solution in vessel 21 to flow between zones 22 and 23 through the lower communicating portions thereof.
• Gas inlet means 24 is positioned in zone 22 and gas inlet means 31 is positioned in zone 23 whereby the respective gas streams entering vessel 21 through means 24 and 31 do not mix.
• the gas stream containing hydrogen sulfide enters vessel 21 through inlet means 24 .n zone 22 and passes through the aqueous solution wherein the polyvalent metal chelate catalyst oxidizes the H 2 S to elemental sulfur and the sweetened gas exits vessel 21 through outlet means 25.
• the gas stream entering through inlet means 24 may contain oxygen which at . least in part simultaneously oxidizes the reduced polyvalent metal chelate to its oxidized form in zone 22. However, if insufficient oxygen is present in the gas stream entering inlet means 24 then additional oxygen can be used in zone 23 to oxidize the reduced polyvalent metal chelate to its oxidized form.
• control valve 34 is opened sufficiently to allow gas to escape from zone 23 thereby drawing the solution from zone 22 into zone 23.
• Zone 23 will normally be equipped with level sensor and controller 35 which controls inlet gas valve 32 and outlet gas valve 34 to thereby maintain the liquid level in zone 23 at the desired level.
• valve 34 will remain closed while oxygen containing gas enters zone 23 through valve 32, thus constantly lowering the liquid level in zone 23.
• a minimum level valve 34 is opened to allow the gas in the top of zone 23 to escape at a high rate compared to the inlet rate at valve 32, thereby raising the liquid level and drawing solution from zone 5 22 into zone 23.
• Maintaining the proper liquid level in zone 23 prevents the solution liquid level from rising too high whereby solution could flow out through outlet means 33 and prevents the liquid level in zone 23 from i ⁇ becoming too low so that gas from inlet 31 could flow from zone 23 into zone 22.
• outlet valve 34 is opened sufficiently to allow the liquid level to rise in zone 23 to draw solution from zone 22 into
• control valve 34 can be closed completely or partially while valve 32 continues to
• zone 25 allow gas to enter zone 23. This forces the liquid level in zone 23 down and the solution from zone 23 back into zone 22. After the liquid level in zone 23 has lowered to the desired low level, but not so low as to cause gas to flow from zone 23 into zone 22, the
• control valves can then be reversed by opening control valve 34 and/or closing or partially closing control valve 32 to again allow the liquid level in zone 23 to rise to the desired level thus drawing solution from zone 22 into zone 23 for oxygen treatment.
• this aspect of the process of the present invention can be operated in any desired manner and in various configurations following the basic principles illustrated in this Figure 2 embodiment of this aspect of the process of this invention.
• the respective shapes and sizes of zones 22 and 23 may be infinitely variable from annular, cylindrical, helical, angular, and the like.
• the basic principle disclosed herein is that the two respective catalyst reduction and oxidation zones only communicate at the lower portion thereof thereby providing means for drawing the solution into the oxidation zone and then expelling the oxidized solution back into the gas treatment zone where the catalyst is again reduced.
• the embodiment illustrated in Figure 2 and the method described above relative to Figure 2 is particularly preferred in order to take advantage of conditions which are desirable for the oxidation of the polyvalent metal chelate catalyst, particularly when incoming gas containing the H 2 S to be removed does not contain sufficient oxygen to keep the polyvalent metal chelate catalyst sufficiently oxidized.
• the oxygen contained in the gas being treated may be stoichiometrically sufficient, but, because of the efficiency of the oxygen transfer into the solution, sufficient oxidation of the polyvalent metal catalyst is not achieved.
• Using the separate oxidation zone as illustrated in Figure 2 and as discussed above is particularly useful in such an instance.
• the separate catalyst oxidation zone illustrated in Figure 2 allows the process to be designed so that the factors important for oxidizing the polyvalent metal chelate solution can be maximized.
• the controlling factor for catalyst oxidation is the mass transfer rate of oxygen from the gas phase into solution.
• gas- liquid contact surface area As important conditions for increased rate of mass transfer are gas- liquid contact surface area, contact time and oxygen partial pressure. Other factors may also affect the mass transfer rate, but these are significant factors.
• small bubbles are important for increasing the surface area and this can be achieved in part by the gas injection sparging means.
• dispersing agents are used to keep the particulate elemental sulfur in suspension and these dispersing agents tend to increase the bubble size and reduce the surface area of contact between the gas and aqueous solution thereby reducing the oxygen mass transfer rate from the gas into dissolved oxygen in the aqueous solution.
• any oxygen present in the gas being treated is normally at a very low level, below about 2000 ppmv, thus the partial pressure of the oxygen in that zone is very low. While sufficient mass transfer of the oxygen from the gas into the solution in zone 22 is sufficient to oxidize part of the reduced polyvalent metal chelate catalyst it is frequently desirable to provide additional oxygen to additionally oxidize the catalyst. This can be most efficiently accomplished in a separate oxidation zone as illustrated by zone 23 in Figure 2.
• gas inlet means 31 can have a different design of sparger or gas inlet means which may provide extremely small bubbles and high gas-liquid surface area contact which might not be feasible for the gas inlet means 24 in gas treatment zone 22.
• the embodiment illustrated in Figure 2 can be operated in such a manner to provide any desired residence time of the solution in oxidation zone 23 before the solution in zone 23 is expelled from zone 23 back into zone 22 then new solution to be treated with oxygen is drawn into zone 23.
• zone 23 can be modified in any desired configuration to provide circulating pumps, baffles, bubble trays or any other conventional or desired means for enhancing the gas liquid contact and the mass transfer of the oxygen from the gas stream into the solution for oxidation of the catalyst.
• the gas-liquid contact time is not par ⁇ ticularly critical in the operation of the present invention provided that sufficient contact time is allowed for the hydrogen sulfide to be absorbed into or dissolved in the aqueous solution. It is necessary that the contact time also be sufficient to allow the oxygen present in the gaseous stream to likewise be absorbed into or dissolved in the aqueous solution.
• conventional contact times for removal of H 2 S from a gas stream by contacting it with a polyvalent metal chelate catalyst solution can be used, such as in the range from about 1 second to about 270 seconds or, more preferably, in the range of about 2 seconds to about 150 seconds, as disclosed in U.S. Patents 4,414,194 and 4,515,764.
• the contact time defined as the volume of the aqueous solution in the vessel divided by the total gas flow rate
• the superficial velocity of the gas stream through the aqueous solution defined as the gas flow rate divided by the cross-section area of the aqueous solution in the vessel.
• the superficial velocity may vary over a wide range, depending on the size and shape of the vessel holding the aqueous solution, one generally useful guideline is to have a superficial velocity in the range of about 0.01 to about 0.15 feet per second.
• the vessel and flow rate for a superficial velocity of about 0.1 foot per second which, when combined with a 5 to 10 foot height of aqueous solution in the contact vessel, will provide a contact time of about 50 to about 100 seconds.
• an increased gas flow rate can reduce the contact time down to about 1 or 2 seconds and still be sufficient for effective removal of the hydrogen sulfide from the gas stream by the process of the present invention.
• the actual superficial velocity and contact time selected for use in the present invention will be deter ined by the mass transfer of the hydrogen sulfide and particularly the oxygen from the gaseous stream into the aqueous solution. Consequently, other conventional factors such as bubble size, flow rates, operating pressures, partial pressures of hydrogen sulfide and. oxygen, as well as the characteristics of the equipment used, such as the gas sparger, mixing baffles, static mixers, etc., all will affect the design criteria for a desired capacity and efficiency of a unit using the process of the present invention.
• Another factor which influences selection of flow rates is the desire in the present invention to minimize foaming and frothing still while maintaining sufficient agitation in the solution to assure full and efficient contact between the gas and the liquid as well as to aid * in preventing settling of the suspended particles of dispersed elemental sulfur.
• the polyvalent metal chelate catalyst useful in the present invention are conventional and well known in the art, as enumerated by the references set forth in the background section of this specification and incorporated herein by reference.
• the preferred metal is generally iron, and the preferred chelating agents are usually aminopolycarboxylic acids such as EDTA, HEDTA, DTPA, NTA as well as sodium salts thereof.
• the buffer materials useful in the present invention for maintaining the pH at the desired level are conventional in the art as described in said references.
• Preferred buffering agents are usually alkaline earth metal bicarbonates, carbonates or hydroxides with the most commonly used being sodium bicarbonate.
• While the process of the present invention will operate at lower levels of sulfur particles in the aqueous suspension without a sulfur dispersing agent present, it is desired for economic commercial operation to include a dispersing agent to enable the operation of the process to higher levels of the dispersed solid sulfur precipitate particles in the aqueous solution, such as levels of about 5 percent to about 8 percent by weight sulfur based on the weight of the aqueous solution or even about 10 percent or more by weight sulfur, before the aqueous solution is discarded and replaced.
• a sulfur dispersing agent is not only desirable in order to keep the particles from agglomerating together, but is also usually desirable because the sulfur particles have a tendency to attach to rising gas bubbles and form a froth or foam at the top of the solution.
• the sulfur particles also tend to be sticky and can foul reactor internals, or can settle and plug the bottom of the reactor.
• Adding .a dispersing agent helps ensure that the sulfur ⁇ will remain homogeneously distributed throughout the aqueous liquid phase due to the minor agitation caused by the rising gas bubbles, and not have a tendency to stick to the process equipment.
• Dispersing agents such as the water soluble sodium salts of ethoxylated monyl phenol half esters of sulfosuccinate acids available from
• the dispersing agent used in the present invention should be those dispersing agents which do not significantly promote foaming and frothing of the sulfur particles.
• Additional dispersing agents which are useful in the present invention will be apparent to one skilled in the art of aqueous dispersions and in particular generally include dispersants which are useful in aqueous pigment systems and are preferably those of lower surface tension properties since increasing the surface tension in the aqueous solution composition system of the present invention may decrease the mass transfer of oxygen and possibly the hydrogen sulfide into the aqueous solution in the process of this invention.
• Dispersants useful in this invention may be selected from the known classes of dispersing agents which are suitable for use in aqueous systems, such as pyrophosphates, saccharin, polyacrylates, aminomethylpropanols, polycarboxylates, polyacrylic acids, salts of carboxylated polyelectrolytes (particularly the "Gradol” 250 and 300 series from Graden Chemical which are non-foaming) , lignosulfonate salts, acetylenic diol blends (particularly the low foaming "Surfynol” TG series from Air Products & Chemicals) , sodium salts of polymeric carboxylic acids (such as the low foaming "Tamol” 850 or 960 from Rohm and Haas Co.) as well as other aqueous system dispersants known in the art.
• dispersing agents which are suitable for use in aqueous systems, such as pyrophosphates, saccharin, polyacrylates, aminomethylpropanols,
• the dispersing agents are typically used in the present invention in the range of about 10 ppmw to about 200 ppmw of the aqueous solution, preferably in the range of about 15 to about 150 ppmw, and most preferably in the range of about 20 to about 100 ppmw in the aqueous solution.
• the dispersing agent may be added to the aqueous solution at the beginning of the process or may be added to the solution after the dispersed sulfur particle content has reached some predetermined level, such as 2, 5 or 8 percent by weight of the aqueous solution. In the present invention it is desirable to keep the average particle size of the precipitated sulfur as small as possible for easier dispersion in the aqueous solution, particularly at higher sulfur content such as 8 to 10 percent by weight or more.
• an anti-foaming agent it is also useful in many instances to use an anti-foaming agent to help prevent frothing or foaming of the solid sulfur precipitate particles in the aqueous solution.
• Some anti-foaming agents tend to promote agglomeration of the sulfur particles and should be avoided because agglomeration and settling of the sulfur- particles are undesirable in the process of the present invention. Therefore, the anti-foaming agents should be selected and used in quantities so that the anti-foaming agent will not unduly promote the agglomeration and settling of the dispersed sulfur particles in the suspension in the aqueous solution. It is usually preferred not to add the anti-foaming agent until it is needed to prevent or dissipate the presence of a foam.
• the anti- foaming agent can be added to the solution at the start of the process.
• settling of the solid sulfur particles can be avoided by keeping the sulfur particles dispersed in suspension or slurry form so that when the aqueous solution is removed from the contact vessel and discarded, all of the elemental sulfur is removed and discarded with the solution.
• the sulfur particle dispersion in the aqueous solution can be aided to some extent by the agitation from the bubbles of the gaseous stream moving upwardly through the aqueous solution.
• anti-foaming agents also may tend to slow the rate at which oxygen is dissolved from the gaseous stream into the aqueous solution. Therefore, the anti- foaming agent should be selected and used in amounts which will not unduly interfere with the mass transfer of the oxygen from the gaseous state into the aqueous solution.
• anti-foaming agents useful in the present invention are the "SAG” GT series from Union Carbide, the "Sulfonal” series from Air Products and the "FG 10" series of silicone anti-foamers from Dow Corning.
• the anti-foaming agents are typically used in the present invention in as small amounts as will provide the desired or necessary control of foaming, which is usually less than about 200 ppmw, more preferably less than about 100 ppmw, and most preferably about 50 ppmw in the -aqueous solution. In many instances, only 5 to 10 ppmw of anti-foaming agent may be needed.
• the anti- foaming agent may be added to the fresh solution at the beginning of the process or may be added at some predetermined point in the process when the weight percent of the solid sulfur precipitate particles reach a certain level, such as 2, 5 or 8 percent by weight. On the other hand, the process can be monitored and the anti-foaming agent added only when foaming is actually present in the contact vessel.
• the gaseous stream was nitrogen containing the above C0 2 , the following amounts of H S and 15.5 volume percent 0 .
• the present invention operating costs are about one-third the costs of operating a sodium nitrite process.
• 500 ppmv H 2 S being reduced to 4 ppmv H 2 S (about 25.5 lbs/day)
• the following comparison can be made:

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• 1989
  • 1989-01-13 JP JP1501986A patent/JPH03503856A/ja active Pending
  • 1989-01-13 EP EP19890902134 patent/EP0398952A4/en not_active Withdrawn
  • 1989-01-13 WO PCT/US1989/000181 patent/WO1989006675A1/en not_active Application Discontinuation
  • 1989-01-13 AU AU30437/89A patent/AU3043789A/en not_active Abandoned
  • 1989-01-13 KR KR1019890701707A patent/KR900700176A/ko not_active Application Discontinuation
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