The disclosure of the present patent application relates generally to the treatment of hydrocarbon gases, and particularly to a system for the removal of acidic, or “sour”, gases from hydrocarbon feeds.
Hydrocarbon gases, such as natural gas, are often extracted from natural gas deposits or reservoirs containing additional acid, or “sour”, gas components, such as hydrogen sulfide (H2S) and carbon dioxide (CO2).
An interchanger 122 is in fluid communication with the contactor 112 for receiving the volume of used absorption liquid solvent. The interchanger 122 heats the volume of used absorption liquid solvent to output a volume of heated solvent, which is fed to a stripper 124. Flow of the heated solvent between the interchanger 122 and the stripper 124 may be controlled by a valve 150.
The stripper 124 receives the volume of heated solvent (“rich” amine) and separates it into an acid gas waste stream and a volume of recycled absorption liquid solvent (a “lean” amine) The acid gas waste stream is fed through an acid gas condenser 102 for lowering its temperature prior to being fed to a reflux drum 152 where, under the power of a reflux pump 154, the acid gas waste stream is output for collection. Reflux water from the refluxing in reflux drum 152 is driven by the reflux pump 154 to feed into the stripper 124, as shown. The reflux water is combined with wash water output from the contactor 112 (under the control of valve 160) for input into the stripper 124.
The lean amine exiting the stripper 124 is fed through the interchanger 122, where it is used to heat the rich amine stream through heat exchange therewith, exiting the interchanger 122 at a lower temperature. This lean amine is pumped through a lean amine air cooler 104 (by a circulation pump 134) to further lower the temperature of the lean amine. The lean amine is then cooled even further to an appropriate temperature (approximately 52° C.) by a trim cooler 106, which uses a recirculating stream of cooling water. Following cooling by the trim cooler 106, the absorption liquid solvent (lean amine) is then fed back into the contactor 112. The stripper 124 uses low-pressure saturated steam as a heating source. Saturated steam is provided to a reboiler 136 from an external source for heat exchange with the stripper 124. The cooled steam exits the reboiler 136 as condensate C.
Conventional acid gas removal systems, such as that described above, consume large amounts of energy during the process of regenerating the rich amine to lean amine, typically on the order of 60% to 70% of the total operating cost of the system. Additionally, conventional amines used in acid gas removal have relatively low CO2 loading capacities, thus requiring the use of high pressure absorber columns, high solvent circulation rates, and consequently large size contactors and strippers. The operating temperatures, pressures and size of the equipment, as well as the choice of amine, contributes to relatively high rates of equipment corrosion, and typically amines must be replaced frequently due to their degradation into organic acids. Typical amine solvents also present a problem, in that there is often co-absorption of valuable product hydrocarbon compounds, such as benzene, toluene, ethylbenzene and xylene.
Thus, an acid gas removal system for removing acidic gases from gaseous hydrocarbons solving the aforementioned problems is desired.
The acid gas removal system for removing acidic gases from gaseous hydrocarbons removes (or “sweetens”) acidic or “sour”, gases, such as hydrogen sulfide (H2S) and carbon dioxide (CO2), from an input gaseous stream, resulting in a “sweetened” or “sweet” gas product. The acid gas removal system includes a contactor having a gas inlet, a gas outlet, an absorption liquid inlet and an absorption liquid outlet. The contactor receives a gaseous stream through the gas inlet and an absorption liquid solvent through the absorption liquid inlet. The absorption liquid solvent contacts the gaseous stream to remove acidic gases therefrom. A treated gas stream is output from the contactor through the gas outlet, and a volume of used absorption liquid solvent is output from the contactor through the absorption liquid outlet. The absorption liquid solvent is preferably methyl diethanolamine (MDEA) with a piperazine (PZ) additive.
A first heat exchanger, such as a plate-plate type heat exchanger or economizer, is in fluid communication with the contactor for receiving the volume of used absorption liquid solvent (rich amine) and heating the volume of used absorption liquid solvent to output a volume of heated solvent. A stripper is in fluid communication with the first heat exchanger for receiving the volume of heated solvent and separating the volume of heated solvent into an acidic gas waste stream and a volume of recycled absorption liquid solvent. The acidic gas waste stream is fed through the first heat exchanger for heating the volume of used absorption liquid solvent.
A second heat exchanger is in fluid communication with the stripper for receiving the volume of recycled absorption liquid solvent (lean amine) The second heat exchanger may also be a plate-plate type heat exchanger or economizer. The second heat exchanger receives a volume of water from an external source of water for cooling the volume of recycled absorption liquid solvent to form at least a portion of the absorption liquid solvent received by the contactor through the absorption liquid inlet thereof.
These and other features of the present disclosure will become readily apparent upon further review of the following specification and drawings.
Similar reference characters denote corresponding features consistently throughout the attached drawings.
The absorption liquid solvent (ALS) contacts the gaseous stream to remove acidic gases therefrom. A treated gas stream TG from which the acidic gas has been removed is output from the contactor 12 through the gas outlet 16. A volume of used absorption liquid solvent (UALS) (rich amine) is output from the contactor 12 through the absorption liquid outlet 20. Although it should be understood that any suitable type of absorption liquid solvent (ALS) may be used, the absorption liquid solvent (ALS) is preferably methyl diethanolamine (MDEA) with a piperazine (PZ) additive.
A first heat exchanger 22 is in fluid communication with the contactor 12 for receiving the volume of used absorption liquid solvent (UALS). The first heat exchanger 22 heats the volume of used absorption liquid solvent (UALS) to output a volume of heated solvent HS. The first heat exchanger 22 is preferably an economizer or plate-plate heat exchanger. Flow of the used absorption liquid solvent (UALS) between the contactor 12 and the first heat exchanger 22 is controlled by a valve 50.
A stripper 24 is in fluid communication with the first heat exchanger 22 for receiving the volume of heated solvent HS and separating the volume of heated solvent HS into an acidic gas waste stream AG and a volume of recycled absorption liquid solvent (RALS) (lean amine) The acidic gas waste stream AG is fed back through the first heat exchanger 22 for heating the volume of used absorption liquid solvent (UALS). The acidic gas waste stream AG may be any type of acid gas (also sometimes referred to as a “sour gas”), such as hydrogen sulfide (H2S) or carbon dioxide (CO2). Following heat exchange, the acidic gas waste stream AG is fed to a reflux drum 52 where, under the power of a reflux pump 54, the acidic gas waste stream AG is output for collection. Reflux water RW from the refluxing process in the reflux drum 52 is driven by the reflux pump 54 to feed into the stripper 24, as shown. The reflux water RW is combined with the wash water WW output from the contactor 12 (under the control of a valve 60) for input into the stripper 24.
A second heat exchanger 26 is in fluid communication with the stripper 24 for receiving the volume of recycled absorption liquid solvent (RALS). The second heat exchanger 26 also receives a volume of water W from an external source of water for cooling the volume of recycled absorption liquid solvent (RALS) to form at least a portion of the absorption liquid solvent (ALS) received by the contactor 12 through the absorption liquid inlet 18. The flow of water W into the second heat exchanger 26 is controlled by a valve 42. Preferably, the second heat exchanger 26 is also an economizer or plate-plate heat exchanger. As shown, the absorption liquid solvent (ALS) is fed back to the contactor by a circulation pump 34. The required concentration of the absorption liquid solvent (ALS), along with its flow rate, are selected according to the acid gas composition(s), flow rate and required quality of the treated gas TG.
The stripper 24 may use low-pressure saturated steam SS as a heating source. Saturated steam SS is provided to a reboiler 36 for heat exchange with the stripper 24, i.e., the reboiler 36 heats the heated absorption liquid solvent to reverse the absorption process so that the acidic gases can be stripped from the absorption liquid solvent by steam in the stripper 24. Steam cooled in the process exits the reboiler 36 as condensate C. As shown, superheated steam (SHS) from an external source may be provided to a de-superheater 38, which converts the superheated steam (SHS) into saturated steam SS. A reverse pump 46 provides heat exchange between a diverted portion of water W (with flow controlled by a valve 40) and the absorption liquid solvent from the contactor 12, reducing the temperature of the absorption liquid solvent returned to the contactor 12 and producing a first stream of steam 51 from the water W. The heat exchange between water W and the recycled absorption liquid solvent (RALS) in the second heat exchanger 26 results in a second stream of steam S2, and both streams 51 and S2 are fed to de-superheater 38 for converting the superheated steam (SHS) into saturated steam SS.
For an initial temperature of feed gas FG of 35° C., the output temperature from the contactor 12 feeding into the reverse pump 46 is approximately 106° C. Following heat transfer with water W in the reverse pump 46, the input temperature back into the contactor 12 is approximately 70° C. Due to this heat transfer, for a temperature of water W feeding into reverse pump 46 of 41° C., the temperature of steam 51 feeding into de-superheater 38 is approximately 101° C. Similarly, for 41° C. water W feeding into the second heat exchanger 26, the temperature of steam S2 feeding into de-superheater 38 is also approximately 101° C. This allows the re-circulating feed through the reboiler 36 to have a temperature of approximately 123° C. and, similarly, for the recycled absorption liquid solvent (RALS) being output from the stripper 24 to also have a temperature of approximately 123° C.
In a conventional prior art acid gas removal system, such as system 100, described above with reference to
Additionally, due to the heat exchange from the reverse pump 46, as described above, the used absorption liquid solvent (UALS) exiting the contactor 12 has a temperature of approximately 45° C., whereas the corresponding UALS of the conventional prior art acid gas removal system 100 has a temperature of approximately 58° C. exiting the contactor 112. Correspondingly, the treated gas TG exiting the contactor 12 in the present system 10 will have a temperature of approximately 61° C., whereas the corresponding treated gas of the conventional prior art acid gas removal system 100 will have a temperature of approximately 52° C.
As noted above, the conventional prior art acid gas removal system 100 uses an interchanger 122 for heat exchange between the RALS exiting the stripper 124 and the used absorption liquid solvent (UALS) exiting the contactor 112. In the conventional prior art system 100, the UALS is typically heated from approximately 58° C. to approximately 100° C. by the interchanger 122. The heated UALS is then cooled slightly to approximately 93° C. before being input to the stripper 124. However, as described above, in the acid gas removal system 10, the UALS is heated by the first heat exchanger 22, which raises the temperature of the UALS from approximately 45° C. to approximately 105° C. before being input to the stripper 24.
The acid gas in both the conventional prior art acid gas removal system 100 and the acid gas removal system 10 exits the stripper with a temperature of approximately 110° C. However, in the present system 10, the acid gas AG is circulated through the first heat exchanger 22 for heat exchange with the UALS. This heat exchange lowers the temperature of the acid gas AG to a temperature of approximately 57° C. for refluxing and disposal. In the conventional prior art acid gas removal system 100, however, acid gas is typically routed directly to the reflux drum 152 and must pass through an additional acid gas condenser 102 to lower its temperature. The present system 10 makes this further piece of additional equipment unnecessary.
Additionally, as noted above, the present system 10 preferably uses methyl diethanolamine (MDEA) with a piperazine (PZ) additive as the absorption liquid solvent. This allows for enhanced CO2 loading in the amine. Combining this with the above temperature differences (and corresponding differences in pressure), the present system 10, when compared against conventional prior art system 100, enhances both carbon dioxide and acid gas loading by approximately 62%.
Further, for saturated steam entering the reboiler 36, in either system, the saturated steam must have a temperature of approximately 152° C., a pressure of approximately 5.02 bars, a specific energy of approximately 2,748.81 kJ/kg, a flow rate of approximately 62,247 kg/hour, and a velocity of approximately 15 m/sec. The conventional prior art system 100 is required to generate saturated steam to meet these requirements, thus expending a large amount of energy simply to produce the required saturated steam. In contrast, the present system 10 recycles superheated steam (SHS) (which is already being produced in the plant) and adds this superheated steam (SHS) to streams S1 and S2, which are generated, respectively, by the reverse pump 46 and the second heat exchanger 26. Streams S1 and S2 already each have a temperature of approximately 101° C., with a pressure of approximately 1.05 bars, a specific energy of approximately 2,254.02 kJ/kg, a flow velocity of approximately 15 m/sec and a flow rate of approximately 39,337.5 kg/hour. Thus, the amount of saturated steam generation required in the present system 10 is approximately 62.5% less than that of the conventional prior art system 100, thus reducing regeneration energy consumption.
Further, the present system 10 reduces the required solvent rate by approximately 38%, reduces pumping power by 45%, and eliminates the need for an additional cooling water stream. This comparison between the present system (PS) 10 and the conventional prior art (PA) system 100 is further elaborated in Tables 1 and 2 below. The graph shown in
It is to be understood that the acid gas removal system for removing acidic gases from gaseous hydrocarbons is not limited to the specific embodiments described above, but encompasses any and all embodiments within the scope of the generic language of the following claims enabled by the embodiments described herein, or otherwise shown in the drawings or described above in terms sufficient to enable one of ordinary skill in the art to make and use the claimed subject matter.
Filing Document | Filing Date | Country | Kind |
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PCT/US2018/040971 | 7/6/2018 | WO | 00 |
Number | Date | Country | |
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62529369 | Jul 2017 | US |