Patent Application
20130055895
The invention relates to the use of an absorbent for the purpose of removing CO2 from technical gases.
The removal of CO2 from technical gases is of special importance with regard to the reduction of CO2 emissions, with CO2 being considered the main cause of the greenhouse effect.
Industry often uses aqueous solutions of organic bases such as alkanolamines, for example, as absorbents for the removal of acid-gas components.
The absorbent is regenerated by supplying heat, depressurising or stripping by means of suitable auxiliary agents. Once the absorbent has been regenerated, it can be reused as a regenerated solvent in the absorption of acid-gas components.
Flue gases from the combustion of fossil-fuels are obtained at approximately atmospheric pressure. As the CO2 content in the flue gases is typically around 3 to 13 vol. %, the CO2 partial pressure ranges correspondingly between only 0.03 and 0.13 bar. To achieve an adequate removal of CO2 from the flue gases at such low CO2 partial pressures, a suitable absorbent is to have a very high CO2 absorption capacity. In particular, highest possible absorption capacity should also be ensured already at low CO2 partial pressures.
The absorption capacity of the absorbent largely determines the required circulation flow rate of the absorbent and thus the size and cost of the necessary equipment. As the energy required for heating and cooling the absorbent is proportional to the circulation flow rate, the regeneration energy required for regenerating the solvent will decrease to a significant degree if the circulation flow rate of the absorbent can successfully be reduced.
Beside a high absorption capacity, however, a suitable absorbent should also have an as high stability towards oxygen as possible, as there is always a certain content of oxygen particularly in flue gases. As known from literature, many amine compounds which are normally characterised by favourable absorption properties decompose easily in the presence of oxygen, which will result in a high absorbent consumption on the one hand and to correspondingly high costs on the other hand. The decomposition products obtained will generally produce a considerably increased level of corrosion and in addition a significantly reduced capacity of the absorbent.
Volatile decomposition products such as ammonia, for example, would cause a contamination of the CO2 product and the flue gas leaving the CO2 scrubber with unpermitted emission components. To avoid such emissions, it will be necessary to add further process steps, which will increase the cost of a CO2 scrubbing unit even further.
The use of an absorbent for the removal of acid gases from a fluid stream is known, for example, from US 2007/0264180 A1. Here, it is taught that 1,2 diaminopropane (termed 1,2-propane diamine) of a concentration of 0 to 30 wt. % can be added to the absorbent as an additional activating agent. The use of an aqueous 1,2 diaminopropane solution which acts as an absorbent in itself is not suggested at all.
For this reason, there is a significant demand for an absorbent which, on the one hand, has an as high CO2 absorption capacity as possible at low partial pressures of <1 bar, particularly at <0.2 bar, and which is at the same time as stable towards oxygen as possible and also thermally stable under absorbent regeneration conditions. To meet such demand, i.e. to make such an absorbent available, and to provide such a method for the removal of CO2 from technical gases, these are the aims of the present invention.
The aim is achieved by the use of an absorbent consisting of 1,2 diamino-propane in aqueous solution.
The absorbent generally contains 10 to 90 wt. %, preferably 30 to 65 wt. % 1,2 diaminopropane with reference to the weight of the absorbent.
In an embodiment of the invention the absorbent to be used contains at least one more amine different from 1,2 diaminopropane. Thus the absorbent according to the invention may, for example, contain 5 to 45 wt. %, preferably 10 to 40 wt. % of one or more different amines.
The at least one more amine different from 1,2 diaminopropane is, for example, selected from:
N(R1)2−n(R2)1+n
(R1)2−n(R2)nN—X—N(R1)2−m(R2)m
H2N—R2-NH2
In a preferential embodiment of the invention the tertiary amines which are used in addition to 1,2 diaminopropane are selected from a group comprising tris(2-hydroxyethyl)amine, tris(2-hydroxypropyl)amine, tributanolamine, bis(2-hydroxyethyl)-methylamine, 2-diethylaminoethanol, 2-dimethylaminoethanol, 3-dimethylamino-1-propanol, 3-diethylamino-1-propanol, 2-diisopropylaminoethanol, N,N-bis(2-hydroxypropyl)methylamine (methyldiisopropanolamine, MDIPA), N,N,N′,N′-tetramethylethylene diamine, N,N-diethyl-N′,N′-dimethylethylene diamine, N,N,N′,N′-tetraethylethylene diamine, N,N,N′,N′-tetramethylpropane diamine, N,N,N′,N′-tetraethylpropane diamine, N,N-dimethyl-N′,N′-diethylethylene diamine, 2-(2-dimethylaminoethoxy)-N,N-dimethyl ethane amine; 1,4-diazabicyclo[2.2.2]octane (DABCO); N,N,N′-trimethylaminoethyl ethanol amine, N,N′-dimethyl piperazine and N,N′-bis(hydroxyethyl)piperazine. Further potential tertiary amines are disclosed in WO 2008/145658 A1, U.S. Pat. No. 4,217,236 and US 2009/0199713 A1.
In a further embodiment the sterically hindered amines which are used in addition to 1,2 diaminopropane are selected from a group comprising 2-amino-2-methyl-1-propanol, 2-amino-2-methyl-1-butanol, 3-amino-3-methyl-1-butanol, 3-amino-3-methyl-2-pentanol and 1-amino-2-methylpropane-2-ol. Other sterically hindered amines that can be used are mentioned in WO 2008/145658 A1, U.S. Pat. No. 4,217,236, US 2009/0199713 A1, U.S. Pat. No. 5,700,437, U.S. Pat. No. 6,500,397 B1 and U.S. Pat. No. 6,036,931.
Optionally, the 5, 6, or 7-membered saturated heterocyclic compounds which are used in addition to 1,2 diaminopropane are selected from a group comprising piperazine, 2-methyl piperazine, N-methyl piperazine, N-ethyl piperazine, N-aminoethyl piperazine, homopiperazine, piperidine and morpholine. Other compounds that can be used are described in WO 2008/145658 A1 and US 2009/0199713 A1.
The primary or secondary alkanolamines which are used in addition to 1,2 diaminopropane are advantageously selected from a group comprising 2-amino ethanol, N,N-bis(2-hydroxyethyl)amine, N,N-bis(2-hydroxypropyl)amine, 2-(methylamino)ethanol, 2-(ethylamino)ethanol, 2-(n-butylamino)ethanol, 2-amino-1-butanol, 3-amino-1-propanol and 5-amino-1-pentanol. Other potential compounds are again disclosed in documents WO 2008/145658 A1 and US 2009/0199713 A1.
In a further embodiment of the invention the alkyl diamines which are used in addition to 1,2 diaminopropane are selected from a group comprising hexamethylene diamine, 1,4-diaminobutane, 1,3-diaminopropane, 2,2-dimethyl-1,3-diaminopropane, 3-methylaminopropylamine, 3-(dimethylamino)propylamine, 3-(diethylamino)propylamine, 4-dimethylaminobutylamine and 5-dimethylaminopentylamine, 1,1,N,N-tetramethylethanediamine, 2,2,N,N-tetramethyl-1,3-propane diamine, N,N′-dimethyl-1,3-propane diamine, N,N′bis(2-hydroxyethyl)ethylene diamine. In addition, all components can be used that are identified accordingly in WO 2008/145658 A1 and US 2009/0199713 A1, and here in particular MAPA.
Furthermore the use of the absorbent is characterised by the feature that the fluid stream is brought into contact with one of the before-specified absorbents, the absorbent thus being laden with CO2. This takes place preferentially at a partial pressure of <200 mbar.
The laden absorbent is advantageously regenerated by heating, depressurising, stripping with stripping vapours produced by internal evaporation of the solvent, stripping with an inert fluid or by a combination of two or all of these measures.
The present invention is described below in more detail by means of two examples.
The stability of 1,2 diaminopropane towards the action of oxygen was determined as follows:
The analyses were carried out in a glass apparatus consisting of round-bottom flasks and reflux condensers. The amines were weighed in. An air flow of approx. 12 NI air/hour, pre-saturated with water vapour, was bubbled into the stirred solution at approx. 110° C. over a period of 4 days. To follow up the course of the reaction, daily samples were analysed by gas-chromatography and acid/base titration (0.1 molar hydrochloric acid) to determine the absolute amine content. At the end the flasks were weigh-checked in order to determine the total amount of the solution.
As a result of the pre-saturation of the air with water vapour there was an increase in weight in the flask over the test period. Once the test result had been corrected by the weight increase resulting from the introduced water, it was surprisingly determined after the completion of the test that the concentration of 1,2 diamino-propane (50 wt. %) in the solution was the same as at the beginning of the test. The measurement hence did not prove any change. Correspondingly no colour changes of the 1,2 diaminopropane were observed over the test period. The colour of the 1,2 diaminopropane was light yellow at the beginning and at the end of the test.
In contrast to this, the stability test of a monoethanolamine solution of also approx. 50 wt. % resulted in a final concentration of 44.89 wt. % after 4 days, all other conditions being the same. This corresponds to a solvent loss of approx. 9.6% of the monoethanolamine used during the test period. Correspondingly the colour changes from slightly beige to dark orange.
A static phase equilibrium apparatus was used to measure the synthetic gas solubility (isothermal P-x data) by the synthetic measuring principle. In this assembly the pressure is measured for different gross compositions of a mixture at constant temperature. The thermostated, purified and degassed solvent is pumped into an evacuated and thermostated measuring cell by means of metering pumps which allow demonstrating minor differences in volume. Subsequently the gas is added in small portions. The CO2 then contained in the absorption solution at a defined pressure is calculated under consideration of the gas space.
The CO2 absorption for a CO2 partial pressure of approx. 0.1 bar was determined at a temperature of 40° C.
The results displayed in table 1 show that with identical amine concentration 1,2 diaminopropane (DAP) absorbs approx. 50% more CO2 than the standard scrubbing agent monoethanolamine (MEA) which is used according to the state of the art.
In the same way as for 40° C., the equilibrium concentration of CO2 in aqueous solution was determined for 120°. Under the typical regeneration conditions in the desorption column (120° C. at approx. 0.09 bar CO2 partial pressure) it is then possible to determine the residual load of CO2. If the remaining residual CO2 concentration is considered for determining the so-called cyclic absorption capacity, i.e. the CO2 absorption actually to be reached by the respective solvent, with the absolute CO2 absorption capacity being reduced by the remaining residual CO2 load from the regeneration of the solvent, the cyclic absorption capacity of 1,2 diaminopropane (DAP) amounts to approx. 1.6 the cyclic absorption capacity of monoethanolamine (MEA) with identical weight portions of the respective amine in water.
This proves that the cyclic absorption capacity of 1,2 diaminopropane is even higher than the absolute CO2 absorption capacity relative to monoethanolamine. This indicates that the regeneration of 1,2 diaminopropane—maybe due to the non-straight chain structure of the hydrocarbon groups—achieves lower residual CO2 loads than the comparable MEA. This constitutes a further advantage of the amine according to the invention.
Hence the invention provides a solvent for the absorption of CO2, especially in the range of low CO2 partial pressures and in the presence of oxygen, which is significantly more stable under these conditions on the one hand and has a higher cyclic absorption capacity on the other hand than a comparable solvent according to the state of the art. This proves the specific suitability of the amine according to the invention for the removal of CO2 from technical gases of low partial pressures (<200 mbar).
| Number | Date | Country | Kind |
|---|---|---|---|
| 10 2010 004 073.8 | Jan 2010 | DE | national |
| Filing Document | Filing Date | Country | Kind | 371c Date |
|---|---|---|---|---|
| PCT/EP10/07799 | 12/20/2010 | WO | 00 | 11/7/2012 |
