MICROBIOLOGICAL DESULFURIZATION OF GASES

Abstract: There is disclosed a method for desulfurizing gases by microbiological techniques which involve the use of chemoautotrophic bacteria of the Thiobacillus genus to convert sulfides to sulfates either as a sulfide removal process or as a process for producing biomass. More specifically, the invention involves the use of Thiobacillus denitrificans under anaerobic conditions to oxidize sulfur compounds such as hydrogen sulfide to sulfate compounds. The process may be carried out by various techniques such as in a continuous bioreactor system using an immobilization matrix. The method is particularly applicable to treating natural gas containing hydrogen sulfide and producing a biomass byproduct.

Description: BACKGROUND OF THE INVENTION This invention relates to the desulfurization of gases and, in particular, relates to the microbiological desulfurization of natural gas. Conventional Acid Gas Removal Natural gas from a well may contain a number of undesirable components which must be reduced to acceptable levels prior to distribution and sale. One of the most common problems in the gas industry is the removal of hydrogen sulfide. Hydrogen sulfide is an acid gas which is toxic and quite corrosive in the presence of water. Natural gas destined for the fuel market ordinarily may contain no more than 0.25 grains per 100 standard cubic feet or 4 ppm on a volume basis. There is a wide variety of commercially available acid gas removal processes. These may be organized into three broad groups based on the mechanism of removal, namely, chemical solvent processes, physical solvent processes and solid bed and slurry processes. In chemical solvent processes, the gas stream is normally contacted with a liquid phase containing a reagent which reacts chemically with the acid gas to produce a species which is retained in the liquid phase at one temperature but released at some elevated temperature. The most commercially important process of this type is the amine process. In the amine process after contacting the gas stream, the solvent is heated to 200-300F to liberate H₂S and regenerate the solvent. The H₂S removed from the gas stream is normally flared or converted to elemental sulfur by the Claus or Stretford process. In another type of chemical solvent process, the gas stream is contacted with a liquid phase or solvent containing a reagent which oxidizes hydrogen sulfide to produce elemental sulfur. Sulfur is typically removed by floatation or filtering. The oxidizing agent is then regenerated by aeration of the solvent. In a physical solvent process a natural gas stream is contacted with a liquid phase in which acid gases simply dissolve under pressure while hydrocarbons are excluded. After contacting the gas stream, dissolved acid gases are generally released when pressure is reduced. As in the amine process, physical solvent processes remove and collect acid gases from a natural gas stream; however, further treatment is required to eliminate hydrogen sulfide. In the common solid bed and slurry processes the natural gas stream is contacted with a solid phase which physically adsorbs hydrogen sulfide or chemically reacts with hydrogen sulfide to form an insoluble and non-volatile metallic sulfide which is retained in the bed. An example of a solid bed process is the iron oxide or iron sponge process. In this process the gas stream is contacted with moist iron oxide supported on a bed of wood shavings. Hydrogen sulfide reacts with the iron oxide to form iron sulfide which is retained in the bed. When the iron oxide has been depleted, the bed can be regenerated with oxygen which converts the iron sulfide to oxide and elemental sulfur. Eventually, however, elemental sulfur accumulates to the point that much of the remaining iron oxide surface area is unavailable to H₂S or excessive pressure drop develops. The bed material must then be replaced. Several factors adversely affect the economics of conventional H₂S removal processes. The amine process, for example, is energy intensive due to the high temperatures required for solvent regeneration. Degradation during thermal regeneration can create disposal problems and amine salts produced in the process are corrosive. Also, a sulfur recovery plant may be required. Although a direct conversion process is conceptually less complicated than the amine process, in practice the direct conversion processes currently available are plagued by a complex chemistry which requires close attention, high chemical make-up costs and disposal problems. In addition, the elemental sulfur produced in these processes is generally of such a poor quality that it is a waste product rather than a process credit. There are generally fewer problems associated with physical solvent processes. However, these processes are only economically viable when the acid gases are present at high partial pressures. Also, hydrogen sulfide disposal may significantly impact the economics of a physical solvent process. Furthermore, many of the common physical solvents utilized for acid gas removal do not totally exclude the C₃+ hydrocarbons thus resulting in hydrocarbon loss and a reduction in the heating value of the natural gas stream. Solid bed and slurry processes are generally simple to operate but labor intensive when the bed material must be replaced. In addition, disposal of the reaction product, with certain processes, require a hazardous waste disposal site. Microbial Removal of Hydrogen Sulfide from a Gas Microbiological processes for the removal of hydrogen sulfide from a gas stream have been described previously. One process is described in Japanese Patent Application No. 170,181/82 which utilizes a mixed culture of bacteria from the Beggiatoa and Thiothrix genera. This is an aerobic process with the predominant end product being elemental sulfur. Another process is described in U.S.S.R. Patent No. 986,469 which involves contacting a hydrogen sulfide containing gas with a culture of Thiobacillus thioparus . This is also an aerobic process with the end product being a sulfate. Both of these processes are intended for waste gas clean-up. Given the requirement for oxygen, neither of these processes would be suitable for the treatment of natural gas unless a complicated process were used which provided for the absorption of hydrogen sulfide in a different stage from the oxidation of the hydrogen sulfide so as to prevent oxygen contamination of the gas. Such two stage processes have been described in West DE-C- 3 300 402 and Japanese Patent No. 58,152,488. In these processes H₂S is first precipitated as CuS or FeS, respectively, which is oxidized aerobically to sulfate in a second stage by Thiobacillus ferroxidans . The precipitating agent is regenerated in the second stage. These processes require a very low, corrosion inducing pH in the second stage. A microbial process for the removal of H₂S from a gas stream based on the photosynthetic bacterium Chlorobium thiosulfatophilum as an alternative to the Claus or Stretford process has been proposed. (Cork, D. J., "Acid Gas Bioconversion - An Alternative to the Claus Process," Dev. Ind. Micro., 23 , 379-387 (1982), Cork, D. J. and S. Ma., "Acid Gas Bioconversion Favors Sulfur Production," Biotech. and Bioeng. Symp. No. 12, 285-290 (1982) and Cork, D. J., R. Garunas and A. Sajjad, " Chlorobium limicola forma thiosulfatophilum : Biocatalyst in the Production of Sulfur and Organic Carbon from a Gas Stream Containing H₂S and CO₂," Appl. and Env. Micro., 45, 913-918 (1983)). The process converts H₂S into elemental sulfur and sulfate and claims sulfur and biomass as process credits. However, the requirement for radiant energy is a severe economic disadvantage whether supplied artificially or collected from sunlight. SUMMARY OF THE INVENTION An object of the present invention is to provide a method for desulfurizing gases by microbiological techniques. More particularly, the invention involves the use of chemoautotrophic bacteria of the Thiobacillus genus to convert sulfides to sulfates either as a sulfide removal process or as a process for producing biomass. More specifically, the invention involves the use of Thiobacillus denitrificans under anaerobic conditions to oxidize sulfur compounds such as hydrogen sulfide to sulfate compounds. A particular embodiment of the invention includes the use of specific strains of Thiobacillus denitrificans which will withstand high sulfide concentrations and be resistant to a common biocide. The process of the invention may be carried out by various techniques such as in a continuous bioreactor system. The invention is particularly applicable to treating natural gas containing hydrogen sulfide and producing a biomass byproduct. BRIEF DESCRIPTION OF THE DRAWINGS Figure 1 is a flow diagram of the preferred embodiment of the invention. Figure 2 is a graph showing the effect of temperature on the growth of Thiobacillus denitrificans . Figure 3 is a graph showing the viability of Thiobacillus denitrificans in free suspension in liquid medium without an energy source. DESCRIPTION OF PREFERRED EMBODIMENTS Introduction With the exception of photosynthetic organisms, the majority of the biological world derives energy from the oxidation of organic compounds. However, there exists a group of microorganisms, predominantly bacteria, which may derive metabolic energy and reducing equivalents for biosynthesis from the oxidation of inorganic elements and compounds. These microorganisms may also derive carbon for biosynthesis from an inorganic source such as carbon dioxide. This is termed a chemoautotrophic mode of metabolism. The present invention employs such bacteria and such mode of metabolism in order to remove sulfides from gas streams. A microbial gas desulfurization process offers several advantages which make the process commercially viable. These include the following: 1. Direct conversion of hydrogen sulfide to sulfate is possible with no requirement for secondary sulfur recovery. 2. The energy requirements are low since the process operates at ambient or near ambient temperatures. 3. The nutrient is predominantly inexpensive mineral salts resulting in a low cost for chemicals. 4. The pH is moderate so that there are minimal corrosion problems. 5. No hazardous wastes are generated and there is minimal disposal problems. 6. The process produces a high protein biomass which could represent a salable product. The ideal microorganism upon which to base a microbial hydrogen sulfide removal process must possess several characteristics in addition to the ability to oxidize hydrogen sulfide. The ideal microorganism should have simple nutritional requirements in order to minimize chemical costs. Preferably the organism would be a strict autotroph, that is, the organism would be capable of deriving all of its metabolic needs from inorganic sources. The ideal organism would also be capable of hydrogen sulfide oxidation in an anaerobic environment thereby avoiding possible oxygen contamination of the gas. Preferably, the ideal organism would produce a soluble oxidation product from the hydrogen sulfide in order to facilitate separation of the oxidation product from the biomass. The organism should also be capable of utilizing a highly soluble terminal acceptor that may be easily supplied in high concentrations. (In order to generate metabolic energy, any organism requires the presence of a particular chemical species to accept the electrons generated by the oxidation of nutrients. For most organisms, this species is oxygen. For those organisms capable of growth in an oxygen free environment, another chemical species is substituted which, in the case of the present invention, is supplied by the oxides of nitrogen.) The ideal organism would also exhibit a small size and simple morphology so that it can be easily maintained in suspension. Many microorganisms produce an extracellular slime layer or capsid which can cause the microorganisms to adhere to walls and to each other. The ideal organism for hydrogen sulfide removal applications should not produce a capsid in order to prevent problems in transport of the organism. A useful organism should also be able to withstand high pressures and to withstand moderately high temperatures. An optimal pH near neutral would be desirable in order to minimize corrosion. Of course, the ideal microorganism would also exhibit a high rate of hydrogen sulfide oxidation per unit biomass. Many chemolithotrophic bacteria are capable of utilizing the oxidation of elemental sulfur and reduced or partially reduced sulfur compounds as a source of energy and reducing equivalents. However, taking into consideration the above factors, the bacterium Thiobacillus denitrificans have been discovered to be uniquely suitable for the objects of the present invention. Thiobacillus denitrificans Thiobacillus denitrificans (T. denitrificans) was first isolated in 1904 by innoculation of an aqueous medium containing MgCl₂, K₂HPO₄, KNO₃, Na₂CO₃ and a sediment of elementary sulfur and CaCO₃ with canal water or mud. A bacterial flora developed which oxidized the sulfur to sulfate and simultaneously reduced nitrate to elemental nitrogen. This was the first evidence of the existence of a chemolithotrophic bacterium which could survive in the absence of oxygen. It was subsequently shown that thiosulfate could be substituted for elemental sulfur. It was later demonstrated that a reduced nitrogen source was required for growth and T. denitrificans was cultivated in a defined medium for the first time. (Baalsrud, K. and K. S. Baalsrud, "Studies on Thiobacillus denitrificans ," Arch. Mikro., 20 , 34-62 Mikro., 20 , 34-62 (1954)). This achievement led to the first thorough study of the growth characteristics of the bacterium. These same authors reported the following: 1) T. denitrificans is a facultative anaerobe utilizing oxygen under aerobic conditions or nitrate under anaerobic conditions as terminal electron acceptor. 2) T. denitrificans is an obligatory autotroph; that is, it cannot derive its metabolic needs from organic sources but is strictly dependent upon elemental sulfur and reduced sulfur compounds as energy sources and carbon dioxide as a carbon source. 3) Nitrate cannot serve as a sole source of nitrogen. Ammonia nitrogen is required for growth. 4) Iron is required for growth. Good growth was reported in media containing 0.25-8.3 micrograms Fe/ml. 5) The optimum pH for growth of T. denitrificans is in the range of 6.2-7.0. The organism is rapidly deactivated below pH 6.0. Although it has been amply demonstrated that thiosulfate and elemental sulfur may be utilized as energy sources with oxidation to sulfate, the utilization of sulfide as an energy source by T. denitrificans , as well as other Thiobacilli , has been the subject of some controversy in the past. Some investigators have reported that cultures of T. denitrificans provided with sulfide, usually supplied as Na₂S, as the sole energy source failed to show an increase in protein content or sulfate concentration in batch reactors. Others have observed the oxidation of sulfide by whole cells or cell free extracts of T. denitrificans and other Thiobacilli . The deposition of elemental sulfur in growing cultures has been observed causing some investigators to speculate that sulfide was oxidized to elemental sulfur and thiosulfate purely chemically and that these products were the true substrates for the Thiobacilli . It is now apparent that those investigators who reported that T. denitrificans was incapable of growth on sulfide as an energy source came to an erroneous conclusion due to the very high initial sulfide concentrations used in their experiments (5-8 mM). Soluble sulfide is toxic to Thiobacilli , as well as other microorganisms, in elevated concentrations. It has been demonstrated that T. denitrificans will grow anaerobically on sulfide as an energy source if sulfide is used as the growth limiting factor in a chemostat. (Timmer-ten Hoor, A., "Energetic Aspects of the Metabolism of Reduced Sulphur Compounds in Thiobacillus denitrificans ," Antonie van Leeuwenhoek, 42, 483-492 (1976)). Under these conditions, the concentration of sulfide in the culture is maintained at very low levels and sulfide was oxidized to sulfate. Although this work established the ability of T. denitrificans to utilize sulfide as an energy source under anaerobic and sulfide limiting conditions, little was known about the stoichiometry or the specific activity of the organism for H₂S oxidation prior to this work. Growth and Maintenance of Cultures The routine maintenance of T. denitrificans for stock cultures in a medium containing sulfide as an energy source would require continuous or semi-continuous addition of sulfide in such a way that sulfide did not accumulate to inhibitory levels in the culture but sufficient substrate was made available for growth. Although this could be done within the scope of the present invention, the obvious difficulties associated with routine day-to-day maintenance of cultures in a sulfide medium can be avoided by use of a non-toxic substrate, preferably thiosulfate. A typical thiosulfate maintenance medium is given by Tables 1 to 3. The thiosulfate in the maintenance medium is the energy source, nitrate is the terminal electron acceptor, bicarbonate is the carbon source and ammonium is the nitrogen source. The medium also includes a phosphate buffer and sources of various essential mineral nutrients. This maintenance medium is similar to the S-8 medium for Thiobacilli recommended by the American Type Culture Collection except that ammonium chloride has been substituted for ammonium sulfate as the source of reduced nitrogen with an increase in the concentration of ammonium ion, the concentrations of sodium bicarbonate and hydrated magnesium sulfate have been increased and a known source of trace elements has been added. Oxidation of Hydrogen Sulfide To produce a culture of T. denitrificans to be utilized for the removal of H₂S from a gas, the organism would typically be grown in the thiosulfate maintenance medium at 30°C and a pH of 7.0 to an optical density at a wavelength of 460 nanometers (OD₄₆₀) of approximately 1.0. This optical density corresponds to greater than 10⁹ cells per ml. As has previously been indicated, the purpose of this cultivation on thiosulfate is to develop a sufficient concentration of biomass so that hydrogen sulfide can be fed to the reactor at an appreciable rate without exceeding the bio-oxidation capabilities of the biomass. Otherwise, sulfide would accumulate in the culture. While growing on thiosulfate a gas feed of 5 mol % CO₂ in N₂ at a rate of approximately 20 ml/min/l of culture is advisable to ensure continuous availability of a carbon source. The pathways for sulfide and thiosulfate oxidation to sulfate in T. denitrificans are not independent but have two common intermediates. In the presence of thiosulfate the rate of sulfide oxidation would be reduced because of competition for enzymes of the sulfur pathway. Therefore prior to the introduction of H₂S to T. denitrificans cultures, residual thiosulfate must be removed. This may be accomplished by collecting the cells by filtration or centrifugation and resuspension in fresh maintenance medium without thiosulfate. A purge of the suspension with 5% CO₂ in N₂ is advisable to allow residual thiosulfate to be metabolized. Hydrogen sulfide may then be introduced into the reactor at loadings of 4-5 mmoles H₂S/hr/g dry wt. of biomass. It should be noted parenthetically that thiosulfate may also be eliminated by cultivating the cells to the point that all thiosulfate is metabolized. However, under thiosulfate limiting conditions, nitrite, which is toxic to T. denitrificans , has been observed to accumulate in the reactor medium. This leads to unstable behavior during the initial hours of operation. The nitrite is eventually metabolized and eliminated. When H₂S is introduced to a culture of T. denitrificans previously grown on thiosulfate, the H₂S is immediately metabolized with no apparent lag. Under sulfide limiting conditions, less than 0.001 mM of total sulfide can be detected in the reactor medium. Provided then that the feed gas exits the reactor in equilibrium with the medium, very low levels of H₂S in the outlet gas can be achieved (less than 1 ppmv). With 10,000 ppm H₂S in the feed gas at one atmosphere, residence times in the range of 1-2 s are required if the average bubble diameter is approximately 0.25 cm. The introduction of H₂S into a batch T. denitrificans reactor results in the accumulation of sulfate and biomass with a corresponding decrease in the nitrate and ammonium concentrations. No elemental sulfur or nitrite accumulates in the reactor. The stoichiometry of the reaction in a batch reactor is given by Table 4. Certain aspects of the stoichiometry of any microbial process are affected by the environment and the growth rate of the microbial cells. During batch growth these parameters are constantly changing. In a continuous stirred tank reactor (CSTR) system, where a fresh nutrient feed (maintenance medium minus thiosulfate) is fed to the reactor at the same rate at which mixed liquor is removed from the reactor, and where there is complete mixing, the environment and growth rate are held constant. Each of these parameters is controlled by the dilution rate at which the reactor is operated. The dilution rate D is defined by Equation (1) where q is the volumetric flow rate of nutrient to the reactor and v is the culture volume. In a CSTR configuration, the stoichiometric parameters of anaerobic H₂S oxidation by T. denitrificans most affected by dilution rate are the OH⁻/H₂S ratio and the yield of biomass per mole H₂S oxidized. With increasing dilution rates the OH⁻/H₂S ratio will decrease since more buffering capacity from the nutrient feed is available for maintaining pH. For example, at D = 0.029hr⁻¹, OH⁻/H₂S is approximately 1.37. At D = 0.058hr⁻¹, OH⁻/H₂S is approximately 1.24. Yield of biomass will be greater at higher dilution rates since a greater fraction of' substrate (H₂S) supports biosynthesis at higher growth rates. The yield of biomass (Y) in grams dry weight/mole H₂S will be given by Equation (2) where µ = is the specific growth rate of T. denitrificans. The specific growth rated µ is defined by Equation (3) and is equal to the dilution rate for a CSTR configuration. Indications of Upset and Recovery from Upset Conditions Since H₂S is an inhibitory substrate, it is imperative that the H₂S feed rate to a T. denitrificans reactor not exceed the maximum capacity of the biomass for H₂S oxidation. If the H₂S oxidation capacity of the biomass is exceeded, sulfide will accumulate in the reactor medium and inhibit the complete oxidation of H₂S. Reactor upset is first detected by the appearance of nitrous oxide (N₂O) in the reactor outlet gas. N₂O results from the incomplete reduction of nitrate. This is followed by H₂S breakthrough and the accumulation of elemental sulfur in the reactor medium. The upset condition is reversible if exposure to the accumulated sulfide is not prolonged. Reduction in H₂S feed rate following an upset condition will reduce H₂S and N₂O concentrations in the outlet gas to pre-upset levels. In addition, elemental sulfur which accumulated during upset will be oxidized to sulfate upon reduction in H₂S feed rate. The maximum loading of a T. denitrificans culture will be somewhat dependent upon both the metabolic state (growth rate) of the biomass and the environment of the biomass. Maximum loadings in the range of 5.0-8.0 mmoles H₂S/hr/g dry wt. biomass may be expected. Effect of Heterotrophic Contamination The medium described by Tables 1-3 will not support the growth of heterotrophic microorganisms since there is no organic carbon source. However, if aseptic conditions are not maintained in the operation of a T. denitrificans reactor, heterotrophic contamination will develop in the reactor. T. denitrificans releases organic material into the medium in the normal course of growth or through lysis of nonviable cells. This organic material then supports the growth of facultatively anaerobic heterotrophs which are capable of using nitrate as a terminal electron acceptor. In a T. denitrificans CSTR operated nonaseptically, the concentration of heterotrophic contaminants will level off and remain constant after a time. The steady state concentration of contaminant is not surprisingly dependent upon the concentration of T. denitrificans . Contaminant levels of up to 10% of the T. denitrificans concentration can be expected. Although the presence of a heterotrophic contamination can affect the end use of the biomass product of the process, the contamination does not affect H₂S oxidation by T. denitrificans . Characterization of Thiobacillus denitrificans Other factors pertinent to the operation of a microbial gas desulfurization process include the effects temperature and pressure, toxicity of other sulfur compounds which may contaminate the feed gas, effects of accumulating sulfate on cell activity and the effect on viability of maintenance in liquid culture in the absence of an energy source. The optimum temperature for growth of T. denitrificans has been reported as 30°C. However, a temperature profile indicating relative growth rates above and below this optimum has not been published. A temperature profile is necessary to predict the effects of a temperature excursion or temperature gradients on overall and local growth rates in a culture. This can be especially important in the case of an inhibitory substrate where a general or localized decrease in growth rate could result in accumulation of the substrate to toxic concentrations. A temperature profile for T. denitrificans ATCC 23642 growing anaerobically on thiosulfate is given in Figure 1 which indicates optimal growth over a relatively narrow range of temperatures with complete inhibition of growth above 40°C. However, viable counts have shown that at temperatures as high as 45°C, no measurable effect on viability is observed for exposures of up to 5 hours. Growth of T. denitrificans in thiosulfate medium at 30°C at elevated pressures indicates that total pressure has no significant effect on growth at pressures of up to 1800 psig N₂ or 1000 psig CH₄. These results are shown in Table 5. Viability was demonstrated at the conclusion of each test by growth on thiosulfate agar and no heteotropic contamination was indicated in that no growth appeared on nutrient agar. In a microbial gas desulfurization process the microorganisms may be subjected to rapid pressurization-depressurization cycles. Table 6 summarizes the results of rapid pressurization-depressurization at 1250 psig of N₂ on viable count in a culture of T. denitrificans originally grown at that pressure on thiosulfate. Table 6 indicates that repeated pressurization-depressurization has no significant effect on viability. Various sulfur compounds common to natural gas are somewhat toxic to T. denitrificans . Those compounds are methyl mercaptan (CH₃SH₃), carbon disulfide (CS₂), carbonyl sulfide (COS) and dimethyl sulfide (CH₃SCH₃). The order of toxicity to wild type T. denitrificans is CH₃SH>CS₂>COS, CH₃SCH₃. All are toxic at a partial pressure of 26,7kPa (200 mmHg). At partial pressures sufficiently low to be tolerated none are metabolized. As H₂S is oxidized by T. denitrificans , a sulfate salt accumulates in the medium. The counter ion of the sulfate in this salt will be determined by the counter ion of the hydroxide equivalents added to the culture to maintain pH and the counter ion of the nitrate salt which furnishes the terminal electron acceptor. For example, if KNO₃ is the nitrate source and KOH is the alkali used for pH control, the oxidation product of H₂S is primarily present as K₂SO₄. Whether the reactor is operated batchwise or on a continuous basis, the concentration of sulfate salt will be dependent upon the rate of H₂S oxidation per unit volume of culture. The tolerance of T. denitrificans for the accumulating sulfate salt, therefore, has a major influence on the operation of the reactor. Wild type T. denitrificans is tolerant of up to 350 mM K₂SO₄ when grown anaerobically on H₂S. Above approximately 400 mM, incomplete oxidation of H₂S is observed with the accumulation of elemental sulfur and production of N₂O. The organism is less tolerant of Na₂SO₄; however, normal reactor operation is observed at Na₂SO₄ concentrations of 250-300 mM. (NH₄)₂SO₄ causes incomplete H₂S oxidation at concentrations above 150-200 mM. As stated above, another factor pertinent to the operation of a microbial gas desulfurization process is the effect on viability of maintenance in liquid culture in the absence of an energy source as would occur if the gas source were shut off for a period of time. As illustrated by Figure 3, the viable count in a culture of T. denitrificans decreases with time in the absence of an energy source. However, if a working culture contains at least 10⁹ cells/ml, a sufficient number of viable cells will exist after as much as 20 days to provide an adequate innoculum to restart the process if care is taken not to overload the biomass. Another factor which will influence the economics of a microbial gas desulfurization process is the value of the biomass produced. The protein content of T. denitrificans whole cells grown on H₂S is 60% ± 3% by dry weight. This protein content is intermediate between that of soybean meal (51%) and fish meal (72%), the two most commercially important sources of bulk protein. The quality of a bulk protein source as a food supplement is dependent not only upon the protein content but also upon the amino acid composition of that protein. Table 7 gives the amino acid composition of T. denitrificans whole cell protein when the organism is grown on H₂S. Table 8 compares the amino acid composition of T. denitrificans whole cell protein, with respect to the ten essential amino acids in a mammalian diet, to that of soybean meal and fish meal. Table 8 indicates that T. denitrificans whole cell protein, on a g/100 g basis, contains more of nine of these amino acids than soybean meal. The only possible exception is tryptophan which has not been determined for T. denitrificans protein. Fish meal contains greater quantities of isoleucine, lysine, threonine and possibly tryptophan. The cysteine content of T. denitrificans is so low as to be undetectable. Mutant Strains The present invention includes not only the use of wild strains of T. denitrificans such as ATCC 23646 (American Type Culture Collection, Rockville, Maryland), but also mutant strains. For example, sulfide tolerant strains of T. denitrificans are desirable to make the proposed microbial gas desulfurization process more resistant to upset from excess H₂S feed and possibly more tolerant of other sulfur compounds. A biocide resistant strain could provide a means of controlling heterotrophic contamination and therefore produce a microbially pure biomass product without the expense of maintaining aseptic conditions by sterilization of feed streams. Therefore, the term T. denitrificans as used herein and in the claims includes mutations. Continuous Flow Reactor with Biomass Recycle A simple CSTR is an economically impractical reactor configuration with respect to volumetric productivity for the proposed microbial gas desulfurization process except where very small amounts of H₂S are removed. However, a completely mixed, homogeneous environment for the cells is required to avoid localized inhibitory concentrations of sulfide. The most practical reactor configuration presently contemplated for a microbial gas desulfurization process based on T. denitrificans is a CSTR with biomass recycle. Recycle of the biomass allows much higher biomass concentrations to be maintained in the reactor. In addition, with biomass recycle, the hydraulic retention time and biomass retention time are decoupled. Therefore, high dilution rates can be used to replenish the culture medium and control the environment of the cells. Biomass concentration and the quality of the cells' environment will be the two most important variables in maximizing volumetric productivity while maintaining reactor stability. With cell recycle, these two variables are independently controlled. For a CSTR with biomass recycle, the microbial cells must continuously be harvested from the reactor liquid waste stream. The more common methods of continuous harvesting of microbial cells include continuous centrifugation and tangential flow filtration. An alternative to harvesting and recycle of free cell biomass is the use of an immobilized biomass which is the preferred embodiment of the present invention as will be described hereinafter. If the immobilization matrix is sufficiently dense, biomass from the reactor effluent may be harvested by low gravity sedimentation. An immobilization matrix appropriate for growing cells must allow release of new cells into the surrounding medium. Therefore, the reactor effluent will contain both immobilized cells which could be readily recovered and recycled and free cells. If the free cells are to represent a process credit, they must be recovered. Therefore, even when immobilized cells are utilized, a free cell recovery problem still exists. However, since these cells are not recycled back to the reactor, treatment of the process stream (with a flocculating agent, for example) to improve sedimentation properties can be tolerated. The particular immobilization matrix does not form a part of the present invention and any known matrix material may be used which is suitable for the T. denitrificans . By way of example only, see US-A-4 153 510 and 4 286 061. Also, any suitable procedure well known in the prior art for immobilizing T. denitrificans cells on the matrix material can be used in the present invention as long as the cells may grow and divide while releasing new cells from the matrix. Referring now to Figure 1, the immobilized biomass is loaded into the reactor 10 which is filled with maintenance medium without thiosulfate. The hydrogen sulfide containing gas is passed into the reactor through line 12 and the treated gas with the H₂S removed flows out line 14. The maintenance medium and immobilized biomass (the slurry) are stirred by the mixer 16 in order to achieve homogeneity, avoid localized inhibitory concentrations of sulfide and obtain good mass transfer. Withdrawn from the reactor 10 is a slurry stream 18 which contains partially spent nutrient, free floating bacteria which have been expelled from the immobilizing support material and the dissolved sulfate formed in the reactor during the H₂S removal process. A form of filtration may be employed to prevent the immobilized biomass from being withdrawn from the reactor along with the slurry. Alternatively, immobilized biomass withdrawn from the reactor along with the slurry is removed from the slurry in separator 20 and recycled to the reactor through line 22. This separator 20, for example, may be a conventional settling basin or hydrocyclone. The slurry from the separator 20 is then passed to the settler 24 through line 26 to form the removal of the free cell bacterial biomass. The preferred method of accomplishing this removal is by introducing a flocculating agent as indicated at 28 into the slurry to assist in the agglomeration and settling of the bacterial biomass. The bacterial biomass product is then removed from the settler as indicated at 30. The remaining liquid from the settler 24 now contains the spent nutrient and the sulfate. This liquid is passed through line 32 into the evaporator/fractional crystallizer 34. In the evaporator/fractional crystallizer, the process is controlled depending upon the relative concentrations of the sulfate and the remaining nutrients in the liquid such that only the sulfate is crystallized or such that the crystallized sulfate will contain only that amount of nutrient which has also been crystallized which can be tolerated in the sulfate product depending upon its intended end use. The product from the evaporator/fractional crystallizer 34 is passed through line 36 to the separator 38 where the crystals are separated from the remaining liquid. The separated crystals containing primarily the sulfate is removed from the settler 38 through line 40. The liquid from the settler 38 contains primarily only the remaining nutrient materials which were present in the withdrawn spent nutrient. This liquid is recycled through line 42 to the reactor 10 along with fresh nutrient introduced through line 44 to replenish the spent nutrient. As shown in Figure 1, the system for practicing this invention includes a temperature controlling heat exchanger 46 in which the medium being fed into the reactor 10 is controlled to a temperature of about 30°C if wild type T. denitrificans is utilized or a higher temperature if a temperature tolerant strain is utilized. It may also be advantageous to precondition the makeup medium being introduced through line 44 to the optimal temperature. Further measures which can be employed to control temperature is to precondition the entering gas 12 to the optimal temperature, include a heat exchanger within the reactor 10 and insulate reactor 10. For the purpose of giving a specific example of the present invention, the treatment of 25 × 10⁶ standard cubic feed/day (7.08 × 10⁸ standard liters/day) of natural gas at 600 psig (42 atmospheres or 4238 kilopascals absolute) containing 1.5 mol % H₂S will be used. At 30°C the volumetric flow of gas at pressure is 1.78 × 10⁷ liters/day. This gas stream will contain 1.87 × 10⁴ gram-mol of H₂S per hour. If a stable loading (sulfide limiting conditions) of 4.0 millimols H₂S per hour per gram biomass is assumed then 4.68 × 10⁶ g of T. denitrificans biomass will be required to treat the gas stream. With a suitable choice of immobilization matrix, immobilized whole cell reactors can be operated with 40% slurries of porous immobilization beads with low rates of attrition. Furthermore, the beads can develop internal populations of viable cells which pack the beads to 50% of their theoretical packing density. However, to be conservative, a 20% slurry of 200 µm beads with a maximum packing density of 25% of theoretical is assumed. This small bead diameter is selected to minimize internal mass transfer resistances. If a T. denitrificans cell is idealized as a cylinder with a diameter of 0.5 µm and length of 1.5 µm, a 200 µm bead would contain 1.67 × 10⁷ cells at maximum packing. A 20% slurry of beads would therefore contain 1.33 × 10¹⁴ cells per liter. A viable cell density of 10⁹ cells per milliliter is roughly equivalent to 0.5 grams dry weight of biomass per liter. Therefore, a 20% slurry of 200 micron beads with maximum cell packing would contain 67 grams per liter of immobilized cells. To be conservative, 50 grams per liter is chosen as a design basis. Therefore, if the free cell biomass is neglected, a total bubble free culture volume of 9.4 × 10⁴ liters will be required to treat the gas stream described above. The economics of a microbial gas desulfurization process are obviously strongly influenced by the volumetric productivity of the bioreactor. A second important factor is the dilution rate at which the reactor is operated. Process economics are favored by lower dilution rates. The reactor effluent must be processed to recover biomass and the sulfate salt, both of which may be taken as a process credit. Lower dilution rates result in a lower rate of flow of the effluent stream and increased concentrations of free cell biomass and sulfate which reduce processing costs. As indicated by Equation (2), the yield of biomass decreases with decreasing dilution rate. However, the higher concentration of biomass in the effluent stream at lower dilution rates could economically offset the reduced yield. In addition, lower dilution rates decrease pumping costs which could be significant given the pressure at which the reactors may operate. However, the reduction of dilution rate to improve process economics has a limitation dictated by the tolerance of the biomass for the accumulating sulfate salt in the culture medium. The maximum concentration of the sulfate salt which can be tolerated without significant inhibition of growth, and therefore H₂S oxidation, will determine the minimum dilution rate at which the reactor can be operated. As noted above, some control can be exerted by choice of the sulfate counter ion which is determined by the nitrate counter ion in the aqueous feed and the hydroxide counter ion in the pH adjusting solution.

Claims: A method for treating a fluid stream containing a sulfide to remove said sulfide comprising the step of contacting said fluid stream under anaerobic conditions with a T. denitrificans culture suspended in a maintenance medium substantially free of thiosulfate whereby said sulfide is removed from said fluid stream by said T. denitrificans and converted to sulfate, and wherein the ratio of fluid stream flow to the quantity of T. denitrificans is such that the average maximum loading of sulfide is no greater than the maximum capacity of the T. denitrificans to remove the sulfide. A method as claimed in Claim 1 wherein said fluid stream is a gas stream and wherein said sulfide is hydrogen sulfide and wherein the process of preparing the T. denitrificans culture suspended in a maintenance medium comprises the steps of: a. culturing T. denitrificans in the absence of H₂S in a maintenance medium containing a quantity of thiosulfate to produce a desired population of T. denitrificans, thereby reducing said quantity of thiosulfate and forming a slurry of T. denitrificans in maintenance medium; b. removing any thiosulfate which may remain in said slurry, and c. introducing said slurry containing said population of T. denitrificans into a reactor containing maintenance medium free of thiosulfate. A method as claimed in Claim 2 wherein the step of contacting the gas stream with the culture comprises the steps of: a. flowing said gas stream through said slurry in said reactor whereby said T. denitrificans removes said hydrogen sulfide under anaerobic conditions and produces sulfate and whereby said population of T. denitrificans increases to produce excess T. denitrificans; b. removing a portion of said slurry from said reactor, said slurry containing excess T. denitrificans and sulfate; c. removing at least a portion of said excess T. denitrificans and at least a portion of said sulfate from said removed slurry thereby leaving a remaining slurry; and d. recycling the remaining slurry back to said reactor. A method as claimed in Claim 3 comprising the steps of: a. immobilizing said population of T. denitrificans in immobilization matrices; b. introducing said population of T. denitrificans in said immobilization matrices into the said reactor containing said maintenance medium free of thiosulfate; c. flowing said gas stream through said slurry in said reactor whereby said population of T. denitrificans increases to produce excess T. denitrificans which are released from said immobilization matrices; d. removing a portion of said immobilization matrices from said reactor with the portion of slurry that is removed; e. removing from said slurry and recycling to said reactor said immobilization matrices containing said T. denitrificans and producing a remaining slurry; f. removing from said remaining slurry said excess T. denitrificans to produce a T. denitrificans biomass produce and a spent maintenance medium containing sulfate, and g. removing at least a portion of said sulfate from said spent maintenance medium and recycling said spent maintenance medium back to said reactor. A method as claimed in Claim 4 and further including the step of introducing fresh maintenance medium to said reactor. A method as claimed in Claims 1 to 6 whereby T. denitrificans multiply and comprising the step of recovering said T. denitrificans as a single cell protein product. A method as claimed in Claims 1 to 6 wherein the temperature in said reactor is controlled to about 30°C. A method as claimed in Claims 1 to 7 wherein the ratio of gas stream flow to the quantity of T. denitrificans being such that the average maximum loading of H₂S is no greater than 8 millimoles of H₂S per hour per gram dry weight of T. denitrificans;

Inventors: SUBLETTE, KERRY LYN
Applicants: COMBUSTION ENGINEERING, INC.
Application year: 1986
Main classification: B01D53
IPC codes: B01D53