WO2011100806A1

WO2011100806A1 - Vapour suppression additive

Info

Publication number: WO2011100806A1
Application number: PCT/AU2011/000182
Authority: WO
Inventors: Phil Jackson; Moataz Ibrahim Attalla; Benjamin Jack Ballinger
Original assignee: Commonwealth Scientific And Industrial Research Organisation
Priority date: 2010-02-19
Filing date: 2011-02-21
Publication date: 2011-08-25
Also published as: EP2536482A4; US8609049B2; JP5854519B2; KR20130000393A; CN102869425A; AU2011202257A1; CA2788978A1; US20130052110A1; AU2011202257B2; CN102869425B; EP2536482A1; JP2013519514A

Abstract

A process for removing CO₂ from a CO₂ containing gas stream in which the CO₂ containing gas stream is contacted with an aqueous ammonium solution. The aqueous ammonia solution comprises 0.1 - 40 % w/v, v/v/ w/w ammonia, and a soluble salt at a concentration range of 0.01% - 10% wt or v/v or w/v, the soluble salt having cations selected from the group of group IA, IIA, IIIA and IVA metals with counter anions selected from the group of anion of group VIIA elements, NO₃-, SO₄ ²-, OH-, PO₄ ³- and HCO₃-. The invention also extends to a CO₂ capture solvent comprising an aqueous ammonia solution and the above soluble salt.

Description

Vapour Suppression Additive

Field of the invention

This invention relates to amines and their use in capturing carbon dioxide from gas streams. Background of the invention

There is growing pressure for stationary producers of greenhouse gases to dramatically reduce their atmospheric emissions. Of particular concern is the emission of carbon dioxide (CO₂) into the atmosphere. One method of reducing atmospheric CO₂ emissions is through its capture at a point source and subsequent storage in geological or other reservoirs.

The process for capturing CO₂ from power station and other combustion device flue gases is termed post combustion capture (PCC). The most mature commercially available technology for PCC is solvent-based chemical absorption/release of C0₂. When the widespread rollout of PCC technology is realised, enormous quantities of solvent such as ammonia and amine will be required. To put this in perspective, a typical 2.4 GW generator burning pulverised black coal produces approx. 30-50 tonnes CO_j/min, or 680 kmol/min.

Clearly, the quantity of solvent that will be used cyclically in a PCC plant of this magnitude is unprecedented. The potential environmental impacts of solvents and solvent degradation products (produced via oxidative and thermal processes) needs consideration, especially as release to the local environment through solvent slippage at this scale may be inevitable.

The most attractive physical solvents for C0₂ capture are those having such properties as high thermal stability, extremely low vapour pressures, non- flammability, and non-toxicity. Such materials have the potential to capture C0₂ with minimal solvent loss in the gas stream. The use of solutions of ammonia for removing CO2 from flue gas streams is attractive from a chemistry perspective, with a number of important advantages relative to systems that employ monoethanolamine (MELA) or other amines as the solvent, long-known for recovering CO2 from gas mixtures. These advantages include

1. SOx and NO_x can be absorbed with the possibility of advantageously selling the spent solvent solution as a fertiliser (SO_x and NO_x degrade amine solvents).

2. Ammonia is a low cost chemical, in widespread commercial use. 3. The overall energy required for such a process is projected to be around 40% of that required for MEA systems.

For the ammonia process, the solvent solution consists of ammonium, bicarbonate ions and to a lesser extent, carbonate, in equilibrium with dissolved ammonia (aqueous), and dissolved CO₂ (aqueous). In the absorber, water and ammonia react with CO2 (aqueous) to form bicarbonate ions or ammonium carbamate ions, with the reaction reversed in the stripper by the application of energy. The relevant aqueous phase reactions can be summarized by the following overall equations:

Ammonia is a light molecule (molecular weight = 17 dalton) which is a gas at temperatures above -30 degrees Celsius (at atmospheric pressure), and it is readily dissolved in water. Sparging aqueous ammonia solutions with a gas stream (such as in a post-combustion capture process) will result in ammonia leaving the solution and entering the gas phase. The amount of free ammonia in the gas phase exiting the absorber is proportional to the amount of aqueous ammonia, which is controlled by solution chemistry and thermodynamic factors such as the temperature: higher temperatures increase the amount of ammonia in the gas phase.

The major concern with the ammonia process has been ammonia loss (or "slip") associated with both the absorber and the stripper. One possible approach to mitigating ammonia slip from capture plants is the use of additives to elevate the aqueous ammonia boiling temperature, thus decreasing ammonia loss via a salt- or azeotropic effect.

It is an object of the present invention to overcome or at least alleviate one or more of the problems associated with the use of ammonia as a CO₂ capture solvent.

Reference to any prior art in the specification is not, and should not be taken as, an acknowledgment or any form of suggestion that this prior art forms part of the common general knowledge in Australia or any other jurisdiction or that this prior art could reasonably be expected to be ascertained, understood and regarded as relevant by a person skilled in the art.

Summary of the invention

Accordingly, in one aspect, the present invention provides a process for removing CO₂ from a C0₂ containing gas stream comprising the steps of contacting the CO₂ containing gas stream with a CO₂ capture solvent, the C0₂ capture solvent comprising or consisting of an aqueous ammonium solution; the aqueous ammonia solution comprising 0.1 %wt to 40 %wt ammonia and a soluble salt at a concentration range of 0.01 % - 10% wt, the soluble salt having one or more cations selected from the group consisting of cations of group IA, IIA, IIIA and IVA metals with counter anions selected selected from the group consisting of anions of group VIIA elements, and

and other water-soluble counter-anions, and

absorbing CO2 from the CO2 containing gas stream into the CO2 capture solvent .

In another aspect of the invention, there is provided a CO2 capture solvent comprising or consisting of an aqueous ammonia solution having an ammonia concentration of 0.1 %wt through to 40 %; and a soluble salt at a concentration range of 0.01% - 10% wt, the soluble salt having one or more cations selected from the group consisting of group IA, IIA, II IA and IVA metals with one or more counter anions selected from the group consisting of anions of group VIIA elements, and

or other water-soluble counter-anion.

In a preferred form of the above aspects of the invention, the cations of the soluble salt are cations of one or more elements selected from the group consisting of Li, Na, K, Rb, Cs, Fr, Be, Mg, Ca, Sr, Ba, Ra, and the anions are one or more anions selected from the group consisting of anions of elements F, CI, Br, I, At, and or other water-soluble

counter-anion.

The additive may be a solution of salts, a pure solid, a heterogeneous solid mixture of several salts or a mixture of aqueous salts (salts dissolved in water). The additive may be crystalline, powdered, molten or any other state when added. The salt may also be added as a hydrous crystalline solid ie. the salt is a solid containing water of crystallisation. The salts may also be added as mixed solid salts eg. Na_(X)K(_1-X)CI. The salts may be dissolved in a solvent miscible with water for addition to bulk quantities of aqueous ammonia solution. In preferred forms of the invention, the water soluble salts are added to a concentration of 0.1-5 % wt and most preferably 1-3 %wt. The concentration of the aqueous ammonia solution used for CO2 capture ranges in concentration from 0.1 % wt through to 40 % wt. The sole purpose of the additive is to reduce the amount of dissolved ammonia which is transferred to the gas phase upon absorption of CO2 contained in power station flue gas. The ammonia may be the sole CO2 capture solvent or it may be blended with other solvents. These other solvents may include any CO2 capture amine in any concentration less than the concentration of ammonia in the blended solvent. The chemical structures of some common suitable capture solvents are presented below:

In particular, the additional solvent is selected from the group consisting of MEA (monoethanolamine), DEA (diethanolamine), AMP (2-Amino-2-methylpropanol), MDEA (methyldiethanolamine) and PZ (Piperazine), methyldiethanolamine (MDEA), digiycolamine (DGA), and di-isopropanolamine (DIPA) and blends of two or more thereof. The concentration of these additional solvent in the blended solvent is less than the concentration of ammonia in the blended solvent. Hence in circumstances where a blended solvent may be used the concentration of ammonia in the solvent is in the range of 20-40%wt. In the preferred forms of the invention salt, the cation is one or more selected from cations selected from the group consisting of barium, caesium or rubidium and the anion is chloride,

or nitrate.

As used herein, except where the context requires otherwise, the term "comprise" and variations of the term, such as "comprising", "comprises" and "comprised", are not intended to exclude further additives, components, integers or steps.

Brief description of the drawings / figures

Figure 1 is a graph of the equilibrium headspace pressures above 150 ml solution containing 10 %wt aqueous ammonia and various additives.

Detailed description of the embodiments

The inventors objective is to discover an additive, which, when added to ammonia, will elevate the solution boiling temperature and thus decrease NH₃ loss via a binary azeotropic effect. In this work, calculations have been undertaken on the model systems CH₃COOH-NH₃ (a heat-stable salt), MEA-

Computational method B3LYP/6-31++G(d,p) works well for relative hydrogen bond strengths, and the thermochemical values produced are usually within 10 kJ/mol of experimental results, so it has been used in this instance. The zero point energies were scaled using the Scott/Radom factor of 0.9806, and the vibrational entropy contribution to the partition function was scaled by 1.0015. All results are for a temperature of 298.15 K. With the exception of the calculations,

performed at the G3 level with the Gaussian 03 programme, the GAMESS software running on an SGI-Altix multi-node DDI system located at Docklands, VIC, was used for the calculations. The computational results are presented in Tables 1 (a) and 1(b)

The numbers in Tables 1 (a) and 1(b) can be used to calculate the energy of the reaction:

These numbers are presented in Tables 2. Table 2. Electrostatic-hydrogen bond/ NH₃ reaction energies at 298.15K.

In turn, these values can be used to calculate equilibrium constants using

These values are contained in Table 3.

Table 3. Equilibrium constants for the hydrogen bonded complexes computed to date.

As seen above, the electrostatic bond with sodium, not unexpectedly, is a strong gas-phase bond, and equilibrium lies well towards the association complex, even in the solution phase. Gas-phase charge separation for

CH₃COOH-NH₃ to form CH₃COO^" and requires substantial energy (see

Tables 2(a) and 2(b)), hence the large enthalpy value for the separation of CH₃COOH-NH₃ into these products. The gas phase dipole-dipole interaction for

CH ₃COOH-NH₃ has a strength of about 40 kJ/mol.

Of the alkanolamines investigated, MEA forms as strong an interaction with ammonia as tnshydroxymethylaminomethane, although the equilibrium constant (298 K) suggests tris might slightly favour complexation of ammonia

Clearly, sodium cation favours complexation most strongly, while HC0₃ favours the dissociated product (the hydroxyl group hydrogen is not acidic at all) It is presumed throughout that if complex-formation is preferred, and, if this is reflected in the equilibrium constant, it follows that a higher solvent boiling temperature will be observed together with a reduction in volatility.

Based on this information, ΜΕ Α should work just as well as tris in reducing the volatility of ammonia.

Based on this information, water soluble salts at a concentration range of 0.01 % - 10% wt will be suitable to suppress the volatility of ammonia in solution. Soluble salts which favour vapour pressure suppression include those having one or more cations selected from the group consisting of group IA, IIA, IIIA and IVA metals with one or more counter anions selected from the group consisting of anions of group VIIA elements, and or

other water-soluble counter-anion. These specifically include one or more soluble salts having cations of elements selected from the group consisting of Li, Na, K, Rb, Cs, Fr, Be, Mg, Ca, Sr, Ba, Ra, and anions selected from the group consisting of anions of elements F, CI, Br, I, At, and

or other water-soluble counter-anion.

In order to evaluate the effectiveness of soluble salts in suppressing the volatility of the ammonia, the following experiments were performed.

Experimental procedure for VLE measurements. For aqueous NH3 solutions and vapour suppressors, addition of a suppressor should result in a lower equilibrium headspace pressure if suppression is taking place (compared with the equivalent solution with no suppressor added).

Experiments were conducted to evaluate the vapour suppression of a number of soluble salts and the results are shown in figure 1 in which Run B = BaCI₂; Run C = CsCI; Run R = RbCl; Run A = ammonia and Run THAM = tris(hydroxymethyl)aminomethane, (HOCH₂)3CNH₂. A vapour-liquid equilibrium apparatus is used in these experiments, consisting of a Parr pressure reactor, some pressure sensors, gas lines, thermocouples, control software and a waterbath. The reactor was filled with 150 ml of a solution consisting of 10%wt ammonia and 1 %wt soluble salt added as ionic solids. The solution temperature was allowed to equilibrate while the system was repeatedly evacuated and flushed with nitrogen to purge air from the test sample. Finally, the headspace was evacuated, and pressure above the liquid (in the headspace) was logged until equilibrium is reached (Δρ,ΔΤ = 0 the pressure/temperature remain constant for at least 1 hour).

The values were recorded. Next, a solution of water was assessed under the same conditions (to correct for baseline when aqueous solutions are analysed)

Figure 1 is a graph of the equilibrium headspace pressures above 150 ml solution containing 10 %wt aqueous ammonia and various additives. In reviewing the results in figure 1 , the lower the value, the more favourable the suppression of NH₃. Any absolute pressure values are meaningless, as they were measured with a transmitter which has a range 0-20 bar. The relative values are important. The y-axis values are equal to the difference between the sensor pressure reading and the actual lab pressure (measured using a barometer). Partial pressure of water vapour is 2.3-3.2 kPa (0.02-0.03 atm). The experiments were conducted at room temperature, and the graph running out to 70 hours (asterisk in the Figure legend) reveals the effects of laboratory temperature fluctuations on the measured values.

Mean pressure value for CsCI = 0.153 atm

Corrected for partial pressure of water = 0.123-0.133 atm (av = 0.128 atm) Mean pressure value for ammonia = 0.218 atm Corrected for partial pressure of water = 0.188-0.198 atm (av = 0.193 atm) Average vapour suppression by CsCI 34 % (range = 29-38 %)

The straight horizontal line at absolute pressure approximately 0.254 atm is the mean of 3 repeat aqueous ammonia runs. Run C, Run B and Run R. The results demonstrate a clear vapour suppression effect due to additives C = caesium chloride, B = barium chloride, R = rubidium chloride. The equilibrium pressure attained after 5 hours is lower than the mean equilibrium pressure attained for 10 % wt aqueous ammonia without additives.

It will be understood that the invention disclosed and defined in this specification extends to all alternative combinations of two or more of the individual features mentioned or evident from the text or drawings. All of these different combinations constitute various alternative aspects of the invention.

Claims

The claims defining the invention are as follows:

1. A CO2 capture solvent comprising an aqueous ammonia solution having an ammonia concentration of 0.1 % w/w to 40 % w/v; and a soluble salt at a concentration range of 0.01 % - 10% wt based on the

GO2 capture solvent , the water soluble salt having cations selected from the group of group IA, IIA, IIIA and IVA metals with counter anions selected from the group of anion of group VIIA elements,

2. The capture solvent of claim 1 wherein the cations of the soluble salt is selected from the group consisting of cations of. Li, Na, K, Rb, Cs, Fr, Be, Mg,

Ca, Sr, Ba, Ra, and the anions are selected from the group consisting of anions of elements F, CI, Br, I, At, and

3. The capture solvent of claim 2 wherein the cation is selected from cations of barium, caesium or rubidium.

4. The capture solvent of claim 2 and the anion is chloride, nitrate or

5. The capture solvent of claim 1 or 3 wherein the water soluble salts are added to a concentration of 0.1-5 % wt.

6. The capture solvent of claim 1 or 3 wherein and the water soluble salts are added to a concentration of 1 -3 % wt.

7. The capture solvent of claim 1 or 3 further comprising one or more additional solvents selected from the group of ΜΕΞΑ (monoethanolamine), DEA, diethanolamine, AMP (2-Amino-2-methylpropanol), MDEA

(methyldiethanolamine) and PZ (Piperazine), methyldiethanolamine (MDEA), diglycolamine (DGA), and di-isopropanolamine (DIPA) and blends thereof to form a blended solvent wherein the concentration of the additional solvent or solvents is less that the concentration of ammonia in the blended solvent.

8. A process for removing CO2 from a CO2 containing gas stream comprising the steps of contacting the CO2 containing gas stream with a C0₂ capture solvent solution; C0₂ capture solvent comprising an aqueous ammonia solution comprising 0.1 % w/v, v/v/ w/w to 40 % w/v ammonia, and a soluble salt at a concentration range of 0.01 % - 10% wt or v/v or w/v based on the CO2 capture solvent, the soluble salt having one or more cations selected from the group consisting of group IA, IIA, IIIA and IVA metals with one or more counter anions selected from the group consisting of anion of group VI IA elements, and

; and

absorbing CO2 from the CO2 containing gas stream into the ammonia solution.

9. The process of claim 8 wherein the cations of the soluble salt are cations of one or more elements selected from the group consisting of Li, Na, K, Rb, Cs, Fr, Be, Mg, Ca, Sr, Ba, Ra, and the anions are one or more anions selected from the group consisting of anions of elements F, CI, Br, I, At, and

10. The process of claim 8 wherein the cation is selected from the group consisting of cations of barium, caesium and rubidium.

1 1. The process of claim 9 and the anion is chloride, nitrate or

12. The process of claim 8 or 10 wherein the water soluble salts are added to a concentration of 0.1 -5 % wt.

13. The process of claim 8 or 10 wherein and the water soluble salts are added to a concentration of 1-3 % wt.

14. The process of claim 8 or 10 further comprising an additional solvent selected from the group of MEA (monoethanolamine), DEA, diethanolamine,

AMP (2-Amino-2-methylpropanol), MDEA (methyldiethanolamine) and PZ (Piperazine), methyldiethanolamine (MDEA), diglycolamine (DGA), and di- isopropanolamine (DIPA) and blends thereof to form a blended solvent wherein the concentration of the additional solvent or solvents in the blended solvent is less that the concentration of ammonia in the blended solvent.