Detailed Description
Step a
The process for removing aromatic hydrocarbons (BTX) from a lean acid gas according to the present invention comprises a first step a): mixing the lean acid gas (1) with H in a first absorption zone (2)2S-selective liquid absorbent solution (29) to produce spent H2S and comprises CO2Aromatic hydrocarbons and C4 +A gas stream (3) of aliphatic hydrocarbons, and also comprising co-absorbed C4 +Aliphatic hydrocarbons, aromatic hydrocarbons and CO2Is enriched in H2S absorbent solution (4).
The purpose of step a) is to minimize H in the gas feed2S content so as to obtain a spent H suitable for combustion in an incinerator (33) and discharge into the atmosphere2S (3). The gas (3) leaving the first absorption zone (2) is depleted of H2S and comprises CO2Aromatic hydrocarbons and C4 +An aliphatic hydrocarbon.
H in lean acid gas2The S content is reduced by H2S-selective liquid absorbent solution (29) absorbs H2And (S) is obtained. Thus, at the bottom of the first absorption zone (2), an enriched H is obtained2S in a liquid absorbent solution. However, even if the first absorption step a) is operated at a relatively low pressure (1-8barA), a part of the aromatics and C contained in the lean acid gas (1) is4 +The aliphatic hydrocarbons will be co-absorbed simultaneously by the liquid absorbent solution (29) and will require further treatment.
Within the meaning of the present invention, the lean acid gas preferably comprises:
-75-99.925 mol.% CO2,
-250mol.ppm to 20 mol.% of H2S, preferably 500mol.ppm to 15 mol.% H2S, more preferably 500mol.ppm to 10 mol.% H2S and even more preferably 500mol.ppm to 5 mol.% of H2S,
-500mol.ppm-5 mol.% of C4 +Aliphatic hydrocarbons and aromatic hydrocarbons, and a mixture thereof,
the percentages are expressed in moles on a dry basis relative to the total moles of the acid-lean gas. In practice, the acid-depleted gas is typically saturated with water.
In a preferred embodiment, the process of the invention comprises CO2And less than 20 mol.% H2Lean gas of S is derived from methane (CH)4) And ethane (C)2H6)、CO2、H2S and C4 +Natural gas of aliphatic and aromatic hydrocarbons.
In fact, this natural gas is used as combustible and therefore should not contain any contaminants, such as acid gases (CO)2、H2S). H in natural gas2The specification for the S concentration is very strict and its maximum concentration should be kept below 4ppm mol. On the other hand, CO2Should preferably be kept below 2% depending on the subsequent use of natural gas and legislation. Therefore, it requires treatment daysNatural gas to remove acid gas (CO) contained therein2、H2S). Purified natural gas is then obtained that meets transport, storage and private or commercial use standards, and at the same time also produces a product that contains CO2、H2S and aromatic hydrocarbons and C4 +Acid-lean gases of aliphatic hydrocarbons. This lean acid gas needs to be treated prior to sulfur recovery.
Thus, in preferred embodiments, the CO comprises2And less than 20 mol.% H2The lean acid gas of S is obtained according to the following process, which comprises:
a) will comprise methane (CH)4) And ethane (C)2H6)、CO2、H2S and C4 +The natural gas of aliphatic and aromatic hydrocarbons is contacted with a liquid absorbent solution in an absorption zone to produce depleted H2S and CO2And comprises methane (CH)4) And ethane (C)2H6) And enriched in H2S and CO2And further comprising co-absorbed C4 +Absorbent solutions of aliphatic and aromatic hydrocarbons,
b) subjecting said enriched H2S and CO2And further comprising co-absorbed C4 +Introducing an absorbent solution of aliphatic and aromatic hydrocarbons into a desorption zone, wherein the liquid absorbent solution is recovered and produces a product comprising CO2And less than 20 mol.% H2Lean acid gas of S.
The natural gas used to obtain the acid-depleted gas for the purposes of the present invention comprises C4 +Aliphatic and aromatic hydrocarbons, and with CO2In comparison with a small amount of H2S (e.g. CO)2Quantity ratio of (H)2The amount of S is at least 4 times higher).
Step a) may preferably be carried out in:
a temperature of from 50 to 200 ℃, preferably of from 110 ℃ to 145 ℃, and
-a pressure of 1 to 8barA, preferably a pressure of 1.5 to 3 barA.
H2The S-selective liquid absorbent solution may be any known absorbent conventionally used by those skilled in the art, such as chemical solvents, substancesPhysical solvents and mixtures thereof. When a chemical solvent is used as the liquid absorbent solution, it may be combined with a physical solvent to enhance absorption of contaminants typically present in the lean acid gas.
For example, the chemical solvent may include alkali metal carbonates and phosphates, or alkanolamines, preferably in the form of an aqueous solution.
The alkanolamine is preferably selected from tertiary alkanolamines and sterically hindered alkanolamines. The sterically hindered alkanolamine may be selected from the group consisting of 2-amino-2-methylpropanol, 2-amino-2-methyl-1, 3-propanediol, 2-amino-2-hydroxymethyl-1, 3-propanediol, 2-amino-2-ethyl-1, 3-propanediol, 2-hydroxymethylpiperidine, 2- (2-hydroxyethyl) piperidine, 3-amino-3-methyl-1-butanol and mixtures thereof.
Suitable alkanolamines include Methyldiethanolamine (MDEA), triethanolamine, or one or more dipropanolamines, such as di-n-propanolamine or diisopropanolamine.
The physical solvent may include, for example, substituted or unsubstituted sulfolane or mercaptoethanol.
In a preferred embodiment, H2The S-selective liquid absorbent solution comprises an amine, preferably an alkanolamine, more preferably a tertiary or sterically hindered alkanolamine, even more preferably Methyldiethanolamine (MDEA). Aqueous Methyldiethanolamine (MDEA) is a preferred liquid absorbent solution according to the present invention.
In another preferred embodiment, H2The S-selective liquid absorbent solution may be a mixture of alkanolamine and mercaptoethanol.
Can also be introduced into the liquid absorbent solution to enhance H2S to CO2Of an absorption-selective additive component, such as an acidic component, e.g. phosphoric acid (H)3PO4)。
The concentration of the aqueous alkanolamine solution can vary widely and one skilled in the art can adjust the solution concentration to achieve a suitable level of absorption. Generally, the concentration of alkanolamine in the aqueous solution is 5 to 60 wt.%, preferably 25 to 50 wt.%. If a physical solvent is used as a component of the absorbent liquid, it may be present in an amount of 2 to 50% by weight, preferably 5 to 45% by weight.
The absorption step a) is preferably carried out:
a temperature of from 10 to 100 ℃, preferably a temperature of from 30 to 70 ℃, more preferably a temperature of from 40 to 60 ℃, and
a pressure of from 1 to 8barA, preferably from 1.5 to 4 barA.
Spent H leaving the first absorption zone (2)2The gas stream (3) of S preferably comprises CO2Aromatic hydrocarbons and C4 +Aliphatic hydrocarbons and in particular comprising:
-60-99 mol.% CO contained in the lean acid gas (1)2More preferably 80-98 mol.%,
60-99 mol.% aromatics and C contained in the lean acid gas (1)4 +Aliphatic hydrocarbons, more preferably 80-98 mol.%,
-0.001-20 mol.% of H contained in the lean acid gas (1)2S, more preferably 0.002-5 mol.%.
The depletion H leaving the first absorption zone (2) can then be2The stream (3) of S is transferred to an incinerator (33) where it is burned to destroy the remaining H2S and aromatic hydrocarbons and C contained therein4 +Aliphatic hydrocarbons to meet the air emission standards. Alternatively, depletion H can be2The stream (3) of S is compressed, injected and discharged into underground storage, rather than incinerated and released into the atmosphere.
Enriched H leaving the first absorption zone (2)2The absorbent solution (4) of S also contains co-absorbed C4 +Aliphatic hydrocarbons, aromatic hydrocarbons and CO2. In a preferred embodiment, the enriched H leaving the first absorption zone (2)2The absorbent solution (4) of S comprises:
80-99.999 mol.% of H contained in the lean acid gas (1)2S, more preferably 95-99.99 mol.%,
-0.5-40 mol.% CO contained in the lean acid gas (1)2More preferably 1-15 mol%
-0.5-40 mol.% of C contained in the lean acid gas (1)4 +Aliphatic and aromatic hydrocarbons, more preferably 1-10 mol.%.
Step b
Then the enriched H leaving the first absorption zone (2)2The absorbent solution (4) of S is sent to a non-thermal stripping zone (8) where it is contacted with a stripping gas stream (7), preferably fuel gas, to obtain spent C4 +Aliphatic and aromatic hydrocarbons and comprising H2S and CO2And also comprising H2S and CO2Is enriched in aromatic hydrocarbons and C4 +A stripping gas stream (10) of aliphatic hydrocarbons.
In fact, further to the first absorption step a), H is enriched2The absorbent solution (4) of S also contains co-absorbed C4 +Aliphatic hydrocarbons and aromatic hydrocarbons.
Therefore, the object of step b) is to use as little H as possible2S, removing as much C as possible from the absorbent solution4 +Aliphatic hydrocarbons and aromatic hydrocarbons such that when a lean acid gas is recovered, it is free of high concentrations of impurities that can poison the sulfur recovery unit catalyst. This is achieved by enriching H in a non-thermal stripping step2The absorbent solution (4) of S is contacted in countercurrent with a stripping gas stream (7), such as a fuel gas stream.
The stripping step of the prior art is usually enriched in H simply by heating2The absorbent solution of S is either produced as a stripping fluid or by direct injection of the fluid in the stripping zone. Supplying heat to the stripping zone increases the acid gases, particularly H, from the absorbent solution2Chemical desorption of S and its removal with a stripping stream is facilitated. Thus, substantial depletion of H is obtained by a conventional stripping step of the prior art2Absorbent solution of S. In contrast, the stripping step of the claimed process is in a sense non-thermal, at which stage no significant heat or energy is provided to the process. By operating the stripping step without significant heating, H can be more selectively stripped2C above S4 +Aliphatic and aromatic hydrocarbons to obtain depleted C4 +Aliphatic and aromatic hydrocarbons and comprising H2S and CO2And also a small amount of H, and2s, but significantly less than H from the thermal stripping step2Enrichment of S with aromatics and C4 +A stripping gas stream (10) of aliphatic hydrocarbons.
The resulting absorbent solution (9) is depleted in C4 +Aliphatic hydrocarbons and aromatic hydrocarbons. The stripping gas stream (7) will preferentially enrich from H2Removal of (strip off) H from S absorbent solution (4)2C above S4 +Aliphatic and aromatic hydrocarbons, but also a portion of H which will be contained in the absorbent solution (4)2S and CO2And (4) carrying away. Thus, the stripping gas stream (10) leaving the stripping zone (8) is enriched in aromatics and C4 +Aliphatic hydrocarbons, and also comprises H2S and CO2。
The stripping gas stream used in the stripping zone of the process of the present invention may preferably be a fuel gas stream, but may also be any combustible gas that meets the requirements of combustible standards, such as natural gas, hydrogen, and/or comprises predominantly H2And CO, or other inert gases containing primarily nitrogen or helium. Thus, the fuel gas or any combustible gas used in the stripping zone can be used as feed/combustible in the incinerator (33) and/or in the utility boiler.
In a preferred embodiment, the stripping gas stream is a fuel gas, and preferably the fuel gas (7) used in the stripping zone (8) is a combustible gas for an incinerator (33) and/or utility boiler in the operating unit. In practice, the plant in which the process of the invention is carried out generally comprises incinerators and/or utility boilers for various purposes. The incinerator and boiler must be supplied with fuel gas. One advantage of the present invention is that the fuel gas required for feeding the incinerator and/or utility boiler of the plant is first used as a stripping gas stream and then recovered and re-routed to its original path for feeding the incinerator and/or utility boiler. The utility boiler (not shown in the figures) generates steam which can be fed to the boiler of the plant in which the claimed process is carried out, for example the boiler (18) in fig. 1. The fuel gas flow rate in the stripping zone is limited by the flow of combustible gas required to operate the incinerator (33) and/or utility boiler. In this embodiment, the fuel gas is continuously used as stripping gas stream in the stripping zone (8) and the incinerator and/or utility boilers are operated as combustible gas, which is economically advantageous.
In this stripping step, a stripping gas stream (7) is preferably introduced into the bottom of the stripping zone in order to be enriched with H2Countercurrent contact of the absorbent solution (4) of S.
The absorption step b) is preferably carried out:
a temperature of from 50 to 150 ℃, preferably a temperature of from 60 to 130 ℃, more preferably a temperature of from 70 to 110 ℃, and
a pressure of from 1 to 8barA, preferably from 1.5 to 4 barA.
To enrich H2The absorbent solution of S (4) meets the pressure conditions required in the stripping zone, it may be necessary to pass it through a pump (5) or through a valve before entering the stripping zone.
Enrichment of H in certain cases where installation is limited, for example in terms of the flow rate of the stripping gas stream2The absorbent solution of S (4) may also be raised in temperature by a heater (6) prior to entering the stripping zone (8) to effect removal of aromatics and C4 +An aliphatic hydrocarbon. In this embodiment, the heat supplied to the stripping step should be controlled to increase aromatics and C4 +Removal of aliphatic hydrocarbons while ensuring that there is only a minimal amount of H2S is desorbed from the absorbent solution to avoid obtaining a solution that will be enriched in H2Stripping gas stream (7) of S. In fact, the stripping gas stream (7) is enriched in H2In the case of S, it would be necessary to increase the size of the second absorption zone to ensure complete removal of H2And S. In a preferred embodiment, the temperature increase in heater (6) may be achieved by recycling at least a portion of the H recovered from desorption zone (16) and/or exiting heat exchanger (heater 15) in heater (6)2S-selective liquid absorbent solution (17). Thus, H2The S-selective liquid absorbent solution serves as a heat source for the heater (6).
The stripping gas stream (10) leaving the stripping zone (8) is enriched in aromatics and C, as described above4 +Aliphatic hydrocarbons, but also H2S and CO2. It preferably comprises:
is contained in the entering stripping zone (8)50-99 mol.%, preferably 85-99 mol.%, of aromatic hydrocarbons and C in the absorbent solution (4) of (a)4 +An aliphatic hydrocarbon(s),
-5-40 mol.%, preferably 5-20 mol.% of CO contained in the absorbent solution (4) entering the stripping zone (8)2,
-1-20 mol.%, preferably 1-10 mol.%, of H contained in the absorbent solution (4) entering the stripping zone (8)2S。
The absorbent solution (9) leaving the stripping zone (8) is depleted C4 +Aliphatic and aromatic hydrocarbons, and preferably comprises:
-80-99 mol.%, preferably 90-99 mol.%, of H contained in the absorbent solution (4) entering the stripping zone (8)2S,
-1-50 mol.%, preferably 1-15 mol.%, of aromatic hydrocarbons and C contained in the absorbent solution (4) entering the stripping zone (8)4 +An aliphatic hydrocarbon(s),
-60-95 mol.%, preferably 70-90 mol.%, of CO contained in the absorbent solution (4) entering the stripping zone (8)2。
In a preferred embodiment, the absorbent solution (9) leaving the stripping zone (8) comprises 0.01-10 mol.% of aromatics and C contained in the lean acid gas (1)4 +Aliphatic hydrocarbons, more preferably 0.1-5 mol.%.
Step c
In a second absorption zone (12), the product obtained in step b) also comprises H2S and CO2Is enriched in aromatic hydrocarbons and C4 +Stripping gas stream (10) of aliphatic hydrocarbons with H2S-selective liquid absorbent solution (28) to obtain depleted H2S and comprising aromatic hydrocarbons, C4 +Aliphatic hydrocarbons and CO2And also co-absorbed aromatics, C4 +Aliphatic hydrocarbons and CO2Is enriched in H2S absorbent solution (14), said H2The S-selective liquid absorbent solution is preferably the same as used in step a).
In particular, more than 80% of the enriched aromatics obtained in step b) and C are separated4 +Stripping gas of aliphatic hydrocarbons (10)A stream, preferably more than 90%, more preferably all of the stripping gas stream (10) is passed to the second absorption zone (12).
In fact, further to the stripping step b), the stripping gas stream (10) is enriched in aromatics and C4 +Aliphatic hydrocarbons, but also H2S and CO2。
Therefore, the purpose of step c) is to remove as much H as possible from the stripping gas stream (10)2S to recover a stripping gas stream suitable for further use as a combustible, such as fuel gas for an incinerator (33) and/or a power plant boiler. Alternatively, depletion H can be2The stripping gas stream of S is compressed, injected and discharged into an underground storage reservoir, rather than incinerated and released into the atmosphere. This is achieved by enriching the aromatics and C4 +Stripping gas stream (10) of aliphatic hydrocarbons with H2S-selective liquid absorbent solution (28), said H2The S-selective liquid absorbent solution is preferably used in step a).
E.g. H2The S-selective liquid absorbent solution (28) may be obtained by introducing a main solvent stream (29) into the first absorption zone.
The conditions of temperature and pressure operating in the second absorption zone (12) are preferably the same as those disclosed previously for the first absorption zone in step a).
Optionally, in order to enrich aromatics and C4 +Aliphatic hydrocarbons but also H2S and CO2The stripping gas stream (10) meets the desired temperature conditions in the second absorption zone (12) and it may be necessary to pass through a cooler (11) and optionally a separator to recover the condensed water before it enters the second absorption zone (12).
The stripping gas stream (13) leaving the second absorption zone (12) preferably comprises aromatics, C4 +Aliphatic hydrocarbons and CO2And in particular comprises:
-60-99 mol.% of CO contained in the stripping gas stream (10) leaving the stripping zone (8)2More preferably 80-98 mol.%,
-60-99 mol.% of aromatic hydrocarbons (BTX) and C contained in the stripping gas stream (10) leaving the stripping zone (8)4 +Aliphatic seriesHydrocarbons, more preferably 80 to 98 mol.% and
-0.01-20 mol.% of H contained in the stripping gas stream (10) leaving the stripping zone (8)2S, more preferably 0.02-5 mol.%.
Depleted H leaving the second absorption zone (12)2S and comprising aromatic hydrocarbons, C4 +Aliphatic hydrocarbons and CO2Meets the standard requirements for combustibles such as combustion gases and can therefore be used as a feed to an incinerator (33) and/or a power plant boiler where the associated aromatics (BTX) and C will be destroyed4 +Aliphatic hydrocarbons and residual sulfur species. Alternatively, depletion H can be2The stripping gas stream (13) of S is compressed, injected and discharged into an underground storage reservoir, rather than being incinerated and released into the atmosphere.
Enriched H leaving the second absorption zone (12)2The absorbent solution (14) of S also contains co-absorbed aromatic hydrocarbons (BTX), C4 +Aliphatic hydrocarbons and CO2。
In a preferred embodiment, the enriched H leaving the second absorption zone (12)2The absorbent solution of S comprises:
-1-40 mol.% of CO contained in the stripping gas stream (10) leaving the stripping zone (8)2More preferably from 2 to 20 mol.%,
-1-40 mol.% of aromatics (BTX) and C contained in a stripping gas stream (10) leaving a stripping zone (8)4 +Aliphatic hydrocarbons, more preferably 2 to 20 mol.% and
-80-99.99 mol.% of H contained in the stripping gas stream (10) leaving the stripping zone (8)2S, more preferably 95-99.98 mol.%.
According to the co-absorbed aromatic hydrocarbons (BTX), C therein4 +The amount of aliphatic hydrocarbon can be such that the enriched H leaving the second absorption zone (12)2The absorbent solution (14) of S is recycled back to the stripping zone (8) to replenish the enriched H2S, and/or may be introduced directly into the desorption zone (16) to replenish the aromatic-depleted absorbent solution (9) obtained in step b).
In a preferred embodiment, the enriched H leaving the second absorption zone (12) is2Complete regeneration of the S absorbent solution (14)Recycled to the stripping zone to replenish the enriched H2S absorbent solution (4) in order to reduce the H enrichment sent to the desorption zone (16)2Aromatic hydrocarbons (BTX) and C in absorbent solution (9) of S4 +Content of aliphatic hydrocarbons.
With its H enrichment leaving the first absorption zone2The stripping zone (8) and the second absorption zone (12) are designed to significantly reduce the spent H entering the desorption zone (16) compared to the content in the absorbent solution of S (4) and even compared to its initial content in the lean acid gas (1)2Aromatics (BTX) and C in absorbent solution of S4 +Content of aliphatic hydrocarbons.
Step d
Further depleting C from the stripping zone (8)4 +An absorbent solution (9) of aliphatic and aromatic hydrocarbons, optionally supplemented with enriched H leaving the second absorption zone (12)2An absorbent solution (14) of S is introduced into a desorption zone (16) in which H is introduced2S-selective liquid absorbent solution (17) recovery and production of spent C4 +Of aliphatic and aromatic hydrocarbons comprising H2S and CO2The lean acid gas of (a).
In fact, the absorbent solution (9) leaving the stripping step b) and the second absorption step C) is depleted in C4 +Aliphatic and aromatic hydrocarbons, but still containing H2S and CO2。
The purpose of step d) is therefore to absorb as much H as possible from the absorbent solution (9)2S and CO2To recover purified absorbent solution that can be recycled back to the first and/or second absorption zone. This is done by heating the absorbent solution (9) in a desorption zone (16).
The absorption step d) is preferably carried out:
a temperature of from 50 to 200 ℃, preferably a temperature of from 70 to 180 ℃, more preferably a temperature of from 110 ℃ to 145 ℃, and
a pressure of from 1 to 4barA, preferably from 1.5 to 3 barA.
In a preferred embodiment, the spent C recovered from the stripping zone (8)4 +The absorbent solution (9) of aliphatic and aromatic hydrocarbons may also be presentBefore entering the desorption zone, the temperature thereof is raised by means of a heater (15) in order to reduce the energy consumption of the fluid circulation in the desorption zone. The temperature increase in the heater (15) is preferably obtained by recycling at least a portion of the regenerated liquid absorbent solution (17) recovered from the desorption zone (16) in the heater (15). Therefore, the regenerated liquid absorbent solution (17) serves as a heating medium for the heater (15).
Generating steam in a desorption zone (16) to provide for removal of H from the absorbent solution2S、CO2Hydrocarbons and aromatics such as BTX. The steam may be generated by heat exchange with any heating means (steam, hot oil, furnace, burner, boiler) present in the liquid absorbent solution at the bottom of the desorption zone (16).
Therefore, the desorption zone (16) preferably comprises a boiler (18) of steam circulation at its bottom, so as to allow enrichment with H2And (4) regenerating the absorbent solution of S.
The regenerated liquid absorbent solution (17) leaving the bottom of the desorption zone (16) can then be used as H2The S-selective liquid absorbent solution (29) is returned to the first absorption zone (2) and/or is used as H2The S-selective liquid absorbent solution (28) is returned to the second absorption zone (12).
In order to bring the regenerated liquid absorbent solution (17) into compliance with the temperature and pressure conditions required in the first absorption zone (2) and the second absorption zone (12), it may be necessary to pass it through a heat exchanger (27) and a pump (19) or through a valve before entering the absorption zones.
The lean acid gas (21) leaving the desorption zone (16) also comprises steam and vaporized absorbent solution. Water from the steam and vaporized absorbent solution carried by the lean acid gas (21) leaving the desorption zone (16) may be partially separated from the lean acid gas (21) depleted in aromatic hydrocarbons in the condenser (22) and further captured in a reflux drum (23) as an accumulator. The water and absorbent solution may then be recycled back to the desorption zone (16) by means of a pump (25) to limit the loss of water and absorbent solution. The lean acid gas (26) depleted in aromatics is recovered. Preferably, the condenser is operated at a temperature of more preferably 20 to 70 ℃, even more preferably 40 to 60 ℃.
Depleted of aromatic hydrocarbon (21) or (26)Hydrocarbons and C4 +Aliphatic hydrocarbons, and preferably includes 0.01 to 10 mol.% aromatics (BTX) and C contained in the lean acid gas entering the process4 +Aliphatic hydrocarbons, more preferably 0.1-5 mol.%.
Furthermore, the lean acid gas (21) or (26) depleted in aromatic hydrocarbons recovered at the end of the process of the invention preferably has a higher H than the lean acid gas (1) entering the process2S/CO2A ratio.
In a preferred embodiment, the aromatic-depleted lean acid gas (21) or (26) recovered after the desorption zone (16) can be partially recycled to supplement the lean acid gas (1) entering the process, and/or to supplement the enriched aromatic and C4 +Aliphatic hydrocarbons but also H2S and CO2Of the stripping gas stream (10).
The inventors have the advantage of finding that the particular continuity of the absorption and stripping steps according to the invention makes it possible to obtain a catalyst system comprising less than 20 mol.% H2Removal of large amounts of aromatics, such as BTX and C, from S-lean acid gas4 +Aliphatic hydrocarbons, although these steps alone are not sufficient to achieve this goal. Contrary to expectations of those skilled in the art, the resulting depleted aromatics and C4 +The lean acid gas of aliphatic hydrocarbons is suitable for subsequent sulfur recovery treatment, even if not enriched in H2S reaches a proportion of more than 55 mol.%, which is necessary for correct operation in a Claus furnace (first step of sulfur recovery), which contains sufficiently small amounts of aromatic hydrocarbons, such as BTX and C4 +Aliphatic hydrocarbons to allow a sulfur recovery unit for partial bypass operation of the furnace, or even no thermal step at all. In a preferred embodiment, the stripping gas stream (7) is combustible and its flow rate is adapted to the requirements of the incinerator (33) and/or the power plant boiler.
In a preferred embodiment, the aromatic hydrocarbons such as benzene, toluene, ethylbenzene and xylenes (BTX) and C in the lean acid gas (21) or (26) recovered at the end of the process of the invention4 +The content of aliphatic hydrocarbons should be as low as possible and not higher than 500mol.ppm, preferably from 1 to 500mol.ppm, in order to prevent deactivation of the Claus catalyst in the subsequent sulfur recovery unit.
2Process for recovering sulphur from lean acid gas comprising less than 20 mol.% HS
The resulting aromatic-depleted lean acid gas (21) or (26) is suitable for use as a feed in a sulfur recovery unit (30).
It is therefore another object of the invention to remove the CO from the gas containing stream2And less than 20 mol.% H2A process for recovering sulfur from a lean S gas, the process comprising:
i) pretreatment for aromatics and C removal according to the methods described previously4 +Lean acid gas (1) of aliphatic hydrocarbons to obtain depleted C4 +Aliphatic and aromatic lean acid gases (21) or (26),
ii) at least part of said depletion C4 +The pre-treated lean acid gas (21) or (26) of aliphatic and aromatic hydrocarbons is mixed with an oxygen-containing gas, such as air, to obtain a gas comprising H2A stream of S and oxygen gas,
iii) optionally, introducing part of the resulting aromatic-depleted lean acid gas (21) or (26) and oxygen into the furnace to recover elemental sulfur,
iv) after optional preheating, recycling depleted C from step ii) and optional step iii)4 +The lean acid gas of aliphatic and aromatic hydrocarbons enters a catalytic reactor containing a catalyst system that catalyzes H with oxygen2Direct oxidation of S and/or with sulfur dioxide (SO)2) Catalysis H2Claus reaction of S to recover spent H2S and elemental sulfur (32).
Typically, elemental sulphur is recovered in a condenser.
Step iv) may preferably be repeated several times, more preferably at least twice.
According to the depletion C obtained in the pretreatment step i)4 +H in lean acid gas (21) or (26) of aliphatic hydrocarbon and aromatic hydrocarbon2S content, the sulfur recovery process can be easily modified by those skilled in the art.
When C is exhausted4 +H in lean acid gas (21) or (26) of aliphatic hydrocarbon and aromatic hydrocarbon2When the S content is less than 15 mol.%, the sulfur recovery methodIt may be preferred to be a catalytic direct oxidation process only (without thermal step iii). In this case, the spent C may be introduced into the catalytic reactor before entering the catalytic reactor4 +The lean acid gas (21) or (26) of aliphatic and aromatic hydrocarbons is preheated.
When C is exhausted4 +H in lean acid gas (21) or (26) of aliphatic hydrocarbon and aromatic hydrocarbon2The conventional Claus process coupling the thermal step iii) and the catalytic Claus step iv) can be operated with an S content of between 15 and 55 mol.%. In this case, only a portion of C is typically depleted4 +Acid-lean gases (21) or (26) of aliphatic and aromatic hydrocarbons are fed into the furnace and the remaining acid-lean gases are oxidized directly in the furnace by the burner bypass of the furnace. Taking into account the high content of inert gases, such as CO, in the lean acid gas2And/or N2Such partial bypassing of the burner of thermal step iii) is required to maintain a stable flame in the burner.
Optionally and preferably, the catalytic direct oxidation process may be assisted by an internal cooler such as SmartSulfTMHot coating of the technology etc. proceeds isothermally or pseudo-isothermally. This technique is advantageous for catalytic reactors after Claus thermal step (iii), and even more advantageous for direct oxidation without Claus thermal step (iii), thus H in lean acid gas (21) or (26)2The S content may be considered to be less than 15 mol.%.
SmartSulfTMThe technique is disclosed in detail in the US2013/0129589 document, the entire content of which is incorporated herein by reference.
According to a preferred embodiment, the catalyst is selected from the group consisting of CO2And less than 20 mol.% H2Step iv) of the process for recovering sulphur from the S-lean acid gas comprises and/or is followed by:
iv.1 after optional preheating, subjecting the mixture comprising H2The lean acid gas of S and oxygen is transferred to a first section of the first reactor, which first section comprises a non-cooled adiabatic bed comprising H catalyzed with oxygen2S oxidation and catalysis of H with sulfur dioxide2A first catalyst for S oxidation, wherein the maximum temperature of the adiabatic bed is T1,
iv.2 transferring the lean acid gas from the first portion of the first reactor to a second portion of the first reactor, the second portion comprising a second catalyst, which may be different from the first catalyst, and the second portion being maintained at a temperature T2, wherein T2 ≦ T1 and T2 is above the dew point temperature of elemental sulfur, resulting in depleted H2The air flow of the S is controlled by the control system,
iv.3 depletion of H2The stream of S is transferred to a sulphur condenser to obtain a sulphur depleted stream,
iv.4 optionally preheating the sulphur depleted gas stream,
iv.5 transferring the sulphur depleted gas stream into a first section of a second reactor comprising a non-cooled adiabatic bed comprising the same catalyst as the first section of the first reactor, wherein the first section of the second reactor is operated at a temperature above the dew point of elemental sulphur such that no elemental sulphur deposits as a liquid or solid on the catalyst in the first section of the second reactor,
iv.6 transferring the gas stream from the first part of the second reactor to a second part of the second reactor, which second part of the second reactor comprises the same catalyst as the second part of the first reactor and which second part is maintained at a temperature equal to or below the dew point of elemental sulphur, such that elemental sulphur is deposited as a liquid or solid on the catalyst in the second part of the second reactor and a desulphurised gas stream is obtained which meets the requirements of air emission standards,
iv.7 switching the operating conditions of the first and second reactor after a defined time and simultaneously switching the gas flows so that the previous second reactor becomes the new first reactor and the previous first reactor becomes the new second reactor.
In this preferred embodiment, in steps iv.2) and iv.6), the second part of the reactor may be maintained at a temperature at or below the dew point of elemental sulphur with the aid of an internal cooler, such as a thermocouple.
In this method, steps iv.1-iv.7 correspond to SmartSulfTMProvided is a technique.
Step iv.7 of switching the operating conditions of the first and second reactor and simultaneously switching the gas flow makes it possible to desorb the elemental sulphur condensed on the catalyst operated in the second reactor. In fact, when operating at the first location (at a higher temperature), the second reactor is operated at a higher temperature, thereby desorbing the sulfur condensed on the catalyst when the reactor was previously operated at the second location (at a lower temperature).
The spent H leaving the sulfur recovery unit in step iv) can then be recycled2The lean S gas (32) is transferred to an incinerator (33) where it is combusted to destroy remaining H2S and aromatic hydrocarbons and C contained therein4 +Aliphatic hydrocarbons to meet the air emission standards. Alternatively, depletion H can be2The stream (3) of S is compressed, injected and discharged into underground storage, rather than being incinerated and released into the atmosphere.
The invention will be further illustrated in the following non-limiting examples.
Example 1
The process for recovering sulphur from a lean acid gas (1) as shown in figure 2 is operated using an acid gas comprising:
o 10.0 mol.% of H2S,
O 82.1 mol.% CO2And are and
o 2500mol.ppm of BTX,
o 180mol.ppm of C4 +,
O 7.3 mol.% water, the remainder being other hydrocarbons such as methane, ethane, and propane, and sulfur such as mercaptans.
The lean acid gas is fed to the first absorption zone (2) at a pressure of 1.7bar and a flow rate of 2800 kmol/h. In the first absorption zone (2), the lean acid gas is contacted at 480m3A flow rate of/h, a 45 wt% (11 mol.%) aqueous Methyldiethanolamine (MDEA) solution (29) introduced at a temperature of 45 ℃ and a pressure of 1.55 barA.
The gas stream (3) leaving the first absorption zone (2) at a flow rate of 2145kmol/h comprises:
92.8 mol.% CO2,
ο<100ppm mol of H2S, and
o 3000ppm mol of BTX (representing 92% of the initial amount of BTX in the lean acid gas),
ο230ppm C4 +(represents C in the lean acid gas)4 +All of the initial amounts of),
6.4 mol.% water, the remainder being other hydrocarbons, such as methane, ethane, and propane, and sulfur, such as mercaptans.
The MDEA solution (4) leaving the first absorption zone (2) absorbs almost the entire amount of H in the lean acid gas2S, and co-absorbs about 8% of the BTX originally present in the lean acid gas. The solvent reached a temperature of about 62 ℃.
Subsequently, the MDEA solution (4) leaving the first absorption zone (2) passes through a pump (5) and through a heater (6) to raise its temperature and pressure to enter the stripping zone (8) at a temperature of 92.0 ℃ and a pressure of 5 barA.
As can be seen from fig. 2, the temperature increase in the heater (6) is obtained by recycling the MDEA solution (20) recovered from the desorption zone (16) in the heater (6).
The heated MDEA solution enters a stripping zone (8) where it is contacted countercurrently with a natural gas stream (7) introduced at the bottom of the stripping zone.
The natural gas stream (7) has the following specifications:
-95.0 mol.% of methane,
5.0 mol.% ethane.
It enters the stripping zone under the following conditions:
flow rate: 200kmol/h of the reaction solution,
temperature: at a temperature of 15 c,
o pressure: 7.0 barA.
The stripper was operated at a pressure of 5.0 barA.
The fuel gas stream (10) leaving the stripping zone (8) has the following specifications:
flow rate: 318kmol/h of the reaction solution,
temperature: at a temperature of 90 c,
o 18.5 mol%CO2,
O 6.4 mol.% of H2S, and
o 1275mol.ppm BTX (65% of BTX entering the stripping zone).
Subsequently, the fuel gas stream (10) leaving the stripping zone (8) is passed through a heat exchanger and enters the second absorption zone (12) at a temperature of 45 ℃. In the second absorption zone (12), the fuel gas stream (10) leaving the stripping zone (8) is contacted at 30m3A Methyldiethanolamine (MDEA) solution introduced at a flow rate, a temperature of 45 ℃ and a pressure of 4.0 barA.
The Methyldiethanolamine (MDEA) solution is the same as the solution used in the first absorption zone (2).
The fuel gas stream (13) leaves the second absorption zone (12) at a flow rate of 255kmol/h and has the following composition:
o 19.6 mol.% CO2,
ο<100mol.ppm of H2S, and
1350mol.ppm BTX (85% of BTX entering the second absorption zone of fluid 16, and about 5% of BTX in the method entering fluid 1).
The fuel gas stream (13) meets the standard requirements for combustibles and can therefore be used as a feed in an incinerator (33) and/or a utility boiler, where the associated aromatics (BTX) and C will be destroyed4 +Aliphatic hydrocarbons and residual sulfur species.
Enriched H leaving the second absorption zone (12)2The MDEA solution of S (14) is recycled to the stripping zone to replenish the enriched H2MDEA solution of S (4).
The BTX depleted MDEA solution (9) leaves the stripping zone (8) at a temperature of 87 ℃ and contains 35% of the BTX entering the stripping zone (corresponding to a flow of about 3% of the BTX entering the process).
The BTX depleted MDEA solution (9) is then introduced into a desorption zone (16) equipped with a boiler (18) operating at a temperature of 130 ℃ and a pressure of 2.4 barA.
The regenerated MDEA solution (17) leaving the bottom of the desorption zone (16) is sent back to the first absorption zone (2) and the second absorption zone (12).
The BTX depleted lean acid gas (21) leaving the desorption zone (16) is passed through a condenser (22) and a reflux drum (23).
The temperature of the BTX depleted lean acid gas (26) recovered at the end of the process of the invention is 45 ℃ and the flow rate is 570 kmol/h. It has the following composition:
o 45.5 mol.% CO2,
O 49.2 mol.% of H2S,
O 390mol.ppm BTX (3% of BTX entering the process), and
4.9 mol.% of H2O。
The process of the present invention makes it possible to reduce the BTX content of the treated lean acid gas by 97%. Even if H2The S content is less than 55 mol.%, and the treated lean acid gas is also suitable for subsequent treatment in a sulfur recovery unit.
The acid gas obtained was then used in the Claus process with a 10% stream of acid gas bypassing the thermal step (furnace), and 2 reactors for operating the catalytic step (SmartSulf)TMTechnique) is processed. A sulfur recovery of 99.3% was obtained. 107 tons of bright yellow solid sulfur were recovered daily meeting sulfur recovery standards without further treatment.
Example 2
The process for recovering sulfur from a lean acid gas as shown in fig. 2 operates using an acid gas comprising:
o 0.2 mol.% of H2S,
92.0 mol.% CO2And are and
o 1500mol.ppm of BTX,
o 180mol.ppm of C4 +,
O 7.3 mol.% water, the remainder being other hydrocarbons such as methane, ethane, and propane, and sulfur such as mercaptans.
The lean acid gas is sent to the first absorption zone (2) at a flow rate of 2800 kmol/h. In the first absorption zone (2), the lean acid gas is contacted at 335m3A flow rate of/h, a 45 wt% (11 mol.%) aqueous Methyldiethanolamine (MDEA) solution (29) introduced at a temperature of 45 ℃ and a pressure of 1.55 barA.
The gas stream (3) leaving the first absorption zone (2) at a flow rate of 2580kmol/h comprises:
92.8 mol.% CO2,
ο<100mol.ppm of H2S, and
1510mol.ppm of BTX (92%),
ο195mol.ppm C4 +(represents C in the lean acid gas)4 +All initial amounts of).
6.6 mol.% water, the remainder being other hydrocarbons, such as methane, ethane, and propane, and sulfur, such as mercaptans.
The MDEA solution (4) leaving the first absorption zone (2) absorbs almost the entire amount of H in the lean acid gas2S and co-absorbed about 8% BTX and reached a temperature of about 55 ℃.
Subsequently, the MDEA solution (4) leaving the first absorption zone (2) passes through a pump (5) and through a heater (6) to raise its temperature and pressure to enter the stripping zone (8) at a temperature of 93.0 ℃ and a pressure of 5 barA.
As can be seen from fig. 2, the temperature increase in the heater (6) is obtained by recycling the MDEA solution (20) recovered from the desorption zone (16) in the heater (6).
The heated MDEA solution enters a stripping zone (8) where it is contacted countercurrently with a natural gas stream (7) introduced at the bottom of the stripping zone.
The natural gas stream (7) has the following specifications:
-95.0 mol.% of methane,
5.0 mol.% ethane.
It enters the stripping zone under the following conditions:
flow rate: the concentration of the catalyst is 360kmol/h,
temperature: at a temperature of 15 c,
o pressure: 7.0 barA.
The stripper was operated at a pressure of 5.0 barA.
The fuel gas stream leaving the stripping zone (8) has the following specifications:
flow rate: 465kmol/h and the concentration of the catalyst,
temperature: at the temperature of 93 ℃,
o8.4 mol.% CO2,
O 0.1 mol.% of H2S, and
625mol.ppm BTX (89% of BTX entering the stripping zone).
The fuel gas stream leaving the stripping zone (8) is then passed through a heat exchanger and enters the secondary absorption zone (12) at a temperature of 45 ℃. In the second absorption zone (12), the fuel gas stream leaving the stripping zone (8) is contacted at 12m3Flow rate/h, Methyldiethanolamine (MDEA) solution introduced at a temperature of 45 ℃ and a pressure of 4.0 barA.
The Methyldiethanolamine (MDEA) solution is the same as the solution used in the first absorption zone (2).
The fuel gas stream (13) leaves the second absorption zone (12) at a flow rate of 406kmol/h and has the following composition:
o 9.1 mol.% CO2,
ο<100mol.ppm of H2S, and
o 680mol.ppm BTX (94% of BTX entering the second absorption zone of fluid 16, and about 7% of BTX entering the method of fluid 1).
The fuel gas stream (13) meets the standard requirements for combustibles and can therefore be used as a feed in an incinerator (33) and/or a utility boiler, where the associated aromatics (BTX) and C will be destroyed4 +Aliphatic hydrocarbons and residual sulfur species.
Enriched H leaving the second absorption zone (12)2The MDEA solution of S (14) is recycled to the stripping zone to replenish the enriched H2MDEA solution of S (4).
The BTX depleted MDEA solution (9) leaves the stripping zone (8) at a temperature of 89 ℃ and contains 11% of the BTX entering the stripping zone (corresponding to a flow of about 1% of the BTX entering the process).
The MDEA solution (9) depleted of BTX is then introduced into a desorption zone (16) equipped with a boiler (18) operating at a temperature of 130 ℃ and a pressure of 2.4 barA.
The regenerated MDEA solution (17) leaving the bottom of the desorption zone (16) is sent back to the first absorption zone (2) and the second absorption zone (12).
The BTX depleted lean acid gas (21) leaving the desorption zone (16) is passed through a condenser (22) and a reflux drum (23).
The temperature of the BTX depleted lean acid gas (26) recovered at the end of the process of the invention is 45 ℃ and the flow rate is 160 kmol/h. It has the following composition:
o 90.8 mol.% CO2,
O 3.4 mol.% of H2S, and
o 220mol.ppm BTX (1% of BTX entering the method),
o 5.8 mol.% of H2O。
The process of the present invention makes it possible to reduce the BTX content of the treated acid-lean gas by 99 mol.%. Even if H2The S content is much less than 55 mol.%, and the treated lean acid gas is also suitable for subsequent treatment in a sulfur recovery unit.
The acid gas obtained was then treated by direct oxidation (SmartSulf) in 2 reactorsTMA technique). A sulfur recovery of 98% was obtained. 2 tons of bright yellow solid sulfur were recovered daily that met the sulfur recovery criteria without further treatment.