This disclosure relates to the use of corrosion inhibitors techniques in a solvent-based post combustion capture system.
Combustion flue gases, refinery off gas, and reformate gas, and the production and use of fossil fuels contribute to an increase in emissions of greenhouse gases (GHGs), such as acid gases—especially carbon dioxide (CO2) and other pollutants such as oxides of sulfur (SOx), oxides of nitrogen (NOx), hydrogen sulphide (H2S) and hydrogen chloride (HCl). It is desirable to reduce the emissions of CO2 or the other pollutants. As a result, large sources of CO2 emissions such as coal-fired power plants, refineries, cement manufacturing, and the like have been targeted to attempt to reduce and/or recover the CO2 emitted.
One method of acid gas capture is gas absorption using aqueous amine solutions or ammonia solutions. Typically this method is used to absorb CO2 and H2S from low-pressure streams such as flue gases emitted from power plants. An example of an amine used in this type of process is monoethanolamine, MEA.
In a typical system, CO2 capture by absorption using chemical liquid absorbent involves absorbing CO2 from the flue gas stream into the absorbent flowing down from the top of the absorber column counter-currently with the flue gas stream, which flows upwards from the bottom of the column. The CO2 rich liquid from the absorber column is then pumped through the lean/rich exchanger to the top of the stripper column where CO2 is stripped off the liquid by application of steam through a reboiler thereby regenerating the liquid absorbent. The chemical absorption of CO2 into the liquid absorbent in the absorber is exothermic leading to the release of heat. The stripping of CO2 from the liquid absorbent in the stripper is endothermic and requires external heating. Typically the lowest temperature in the absorber column is no higher than 60° C., which is limited by the temperatures of the lean liquid absorbent and flue gas stream temperatures, and the highest temperature is around 90° C. The typical temperature for stripping or desorption is in the range of 105-150° C. The CO2 desorption process is endothermic with a much higher heat demand than the absorption process can provide thus setting up a temperature mismatch between the absorber and regenerator/stripper.
Aqueous amine-based CO2 capture systems can suffer from significant corrosion problems. Corrosion can affect almost every part of the process equipment depending on operating parameters such as amine type, amine concentration, CO2 loading, process temperature, oxygen concentration, presence of degradation products, and solution velocity. Attempts have been made to minimize corrosion through the design and operation of the plant, the use of corrosion-resistant materials, the removal of corrosion-promoting agents, and the use of corrosion inhibitors.
The use of a corrosion inhibitor can be economical and does not generally require major process modifications for existing plants. Various corrosion inhibitors have been developed and commercialized for use in amine treating units. Inorganic inhibitors have been favoured over organic compounds because of their superior inhibition performance. However, these inorganic corrosion inhibitors (e.g. inhibitors containing toxic arsenic, antimony and vanadium) are not considered environmentally friendly. Vanadium compounds, particularly sodium metavanadate, are used extensively in amine treating plants. This compound can be toxic and is also detrimental to the rate of degradation of the amine (e.g. MEA).
The present disclosure relates to corrosion inhibitors and processes, uses, methods, compositions, devices, and apparatus involving corrosion inhibitors. For example, the present disclosure provides the use of specific corrosion inhibitors, specific concentrations of inhibitors, blends of inhibitors, processes utilizing such inhibitors, and compositions comprising such inhibitors.
The present disclosure provides the use of specific corrosion inhibitors in acid gas separation systems such as aqueous amine- or ammonia-based CO2 separation systems. An example of the mentioned separation processes is the post combustion capture of CO2 from flue gases using amines.
The present technology may be used in a variety of situations. For example, in the treatment of:
The present disclosure may be applied to amine-based or ammonia-based methods for CO2 absorption and/or desorption. This includes using different types of amines and/or absorbents, different process configurations, and using steam and/or hot water to provide the energy that is required for stripping for CO2 capture from flue gas streams, natural gas, reformate gas, etc.
In the description that follows, a number of terms are used, the following definitions are provided to facilitate understanding of various aspects of the disclosure. Use of examples in the specification, including examples of terms, is for illustrative purposes only and is not intended to limit the scope and meaning of the embodiments of the invention herein. Numeric ranges are inclusive of the numbers defining the range. In the specification, the word “comprising” is used as an open-ended term, substantially equivalent to the phrase “including, but not limited to,” and the word “comprises” has a corresponding meaning.
All citations are herein incorporated by reference, as if each individual publication was specifically and individually indicated to be incorporated by reference herein and as though it were fully set forth herein. Citation of references herein is not to be construed nor considered as an admission that such references are prior art to the present invention.
One or more currently preferred embodiments of the disclosure have been described by way of example. The invention includes all embodiments, modifications and variations substantially as hereinbefore described and with reference to the examples and figures. It will be apparent to persons skilled in the art that a number of variations and modifications can be made without departing from the scope of the invention as defined in the claims. Examples of such modifications include the substitution of known equivalents for any aspect of the invention in order to achieve the same result in substantially the same way.
As used herein, the term ‘absorption media’ and ‘adsorption media’ refers to media that can absorb/adsorb an amount of acid gas.
As used herein, the term ‘rich absorption and/or adsorption media’ refers to media that has absorbed/adsorbed an amount of acid gas relative to lean media.
As used herein, the term ‘lean absorption and/or adsorption media’ refers to media that has no or low amounts of acid gas.
Absorption/adsorption media that may be used herein include monoethanolamine (MEA), diglycolamine (DGA), diethanolamine (DEA), methyldiethanolamine (MDEA), 2-amino-2-methyl-1-propanol (AMP), piperazine (PZ), ammonia, amines, alkanolamines, amino alcohols, diamines, ionic liquids, aminosilicone, derivatives and/or combinations thereof.
As used herein, the term ‘acid gas’ refers to gases that form acidic solutions when mixed with water. Examples of acid gases include carbon dioxide (CO2), sulphur dioxide (SO2), sulphur trioxide (SO3), hydrogen sulphide (H2S), hydrogen chloride (HCl), and oxides of nitrogen (NOx).
It has been reported that the corrosion rate of carbon steel in MEA-H2O—CO2—O2—SO2 system increases with increasing MEA concentration, CO2 loading, operating temperature, O2 and SO2 concentrations in the flue gas stream. Several corrosion mechanisms in MEA-H2O—CO2—O2—SO2 system have been postulated. The general anodic reaction in anode site is the dissolution of iron or the oxidation of iron to the ferrous (Fe2+) ion
FeFe2++2e− (1)
There are different types of the reduction reactions (cathodic partial reactions) in MEA-H2O—CO2—O2—SO2 system on the cathode site.
Reduction of dissolved oxygen:
O2+2H2O+4e−4OH− (2)
Reduction of hydrogen ion (H+) or H3O+
2H++2e−H2 or (3)
2H3O++2e−2H2O+H2 (4)
Reduction of carbonic acid (H2CO3) and bicarbonate (HCO3−)
2H2CO3+2e−H2+2HCO3− (5)
2HCO3−+2e−H2+2CO32− (6)
In our study on the efficacy and effect of concentration of various corrosion inhibitors was examined. The experiments were conducted under severe corrosion conditions found in the CO2 capture process in which MEA, O2, SO2 concentrations, and CO2 loading were 7 kmol/m3, 6%, 204 ppm, and 0.5 mol CO2/mol MEA, respectively. The operating temperature of the corrosion experiments was at 353K. This condition represented an uninhibited system. MEA was chosen as the absorption solvent because of its widespread use in CO2 capture process and its corrosiveness. Carbon steel12 was used as a test specimen since it is widely used for construction of equipment in the CO2 capture process. The objective of this work was to screen and test corrosion inhibitors and blends of corrosion inhibitors, including, dodecylamine, sodium molybdate, morpholine, imidazole, and a commercial inhibitor (MAX-AMINE CMX9053 from GE Betz).
The electrochemical experiments were carried out using monoethanolamine (reagent grade with >99% purity, Fisher Scientific, ON) as the absorption solvent. It was diluted with deionized water to the desired concentration, which was accurately determined by titration with 1.0 N hydrochloric acid (HCl) solution using methyl orange as a titration indicator. The desired concentration of aqueous MEA solution was then preloaded with carbon dioxide to obtain the desired CO2 loading (mol CO2/mol MEA) by purging a stream of CO2 gas (Praxair, research grade, ON) into the solution. The CO2 loading procedure followed the AOAC method13. The desired CO2 loading was determined by titrating with the 1.0N HCl solution using a Chittick apparatus.
Carbon steel C1020 (Metal Samples Company, AL) was used to study the corrosion in MEA-H2O—CO2—O2—SO2 system. Its chemical composition in percentage is as follows: C, 0.19; Cr, 0.01; Cu, 0.01; Mn, 0.56; Mo, 0.01; N, 0.0036; Ni, 0.01; P, 0.009; S, 0.007; and Fe, balance. The tested specimens are cylindrical in shape with ⅜″ diameter, ½″ length with a 3-48 threaded hole at one end. The specimens were prepared in accordance with ASTM G1-9014. The specimens were wet ground with 240 grit silicon carbide paper, wet polished with 600-grit silicon carbide paper, rinsed with deionized water, dried with air and kept in a desiccator before use. The surface areas of the specimens were determined by measuring all dimensions with a vernier caliper.
Electrochemical techniques were used to study corrosion and corrosion behaviour of carbon steel C1020 in MEA-H2O—CO2—O2—SO2 system. The experiment setup is shown in
The ASTM G5-9415 was used in evaluating the accuracy of a given electrochemical test apparatus. It was performed by running the experiment with potentiodynamic anodic polarization technique on a stainless steel 430 in 1N sulfuric acid (H2SO4) solution at 30° C. The reliability of experiment is ascertained when the obtained polarization plot appears within the reference band. All of the electrochemical experiments were carried out in accordance with ASTM G5-94.
The Tafel plot technique16,17 was used to evaluate corrosion rate. A Tafel Plot was generated by beginning the scan from −250 mV to +250 mV vs. corrosion potential (ECORR). The resulting data is plotted as the applied potential vs. the logarithm of the measured current. The corrosion current (iCORR) was obtained from the intersection at ECORR, and then was used to calculate the corrosion rate using equation 7.
where CR is the corrosion rate in mpy (mils per year), iCORR is the corrosion current in microampere (μA), E.W. is equivalent weight of the corroding species in gram (g), A is the surface area of the specimen in square centimeter (cm2) and d is the density of the specimen in gram per cubic centimeter (g/cm3).
The inhibition efficiency of corrosion inhibitor was investigated in the system of severe corrosiveness, which was 7 kmol/m3 MEA, CO2 loading of 0.5 mol CO2/mol MEA with simulated flue gas stream of 204 ppm SO2 and 6% O2 at 353K. Its performance was calculated by the following equation18:
where CRuninhibited is corrosion rate of the uninhibited system and CRinhibited is corrosion rate of the inhibited system.
2.4 Corrosion System without Inhibitor
The corrosion cell containing about 1 liter of 7 kmol/m3 MEA, CO2 loading of 0.5 mol CO2/mol MEA was immersed in a water bath with a temperature controller. The temperature of the solution was kept constant at 353 K. A stream of simulated flue gas of 204 ppm SO2 and 6% O2 was introduced into the corrosion cell at the flow rate of 150 ml/min for one and a half hour. The carbon rods counter electrodes were placed in the test cell. Then, the salt bridge was filled with a test solution and placed in the corrosion cell. The prepared surface was mounted on the electrode holder rod. Consequently, the specimen was degreased with methanol and rinsed in distilled water just prior to immersion in the test cell. The salt-bridge probe tip was adjusted close to the specimen electrode. All the lines between the corrosion cell and the Model 273A potentiostat had been connected before the corrosion potential (ECORR) versus the MSE reference electrode of the test system were measured for at least 1 hour to ensure that the corrosion potential value remained constant. Finally, the electrochemical experiment was started. The applied potential and the measured current were continuously recorded.
2.4.2 Corrosion System with Inhibitor.
Various corrosion inhibitors were investigated their inhibition in amine based solvents for CO2 absorption from power plant flue gases containing CO2, O2, and SO2. They were dodecylamine, morpholine, and sodium molybdate. Imidazole and a commercially available inhibitor were also examined.
A known concentration of inhibitor was introduced into the corrosion cell containing 1 liter of 7 kmol/m3 MEA, CO2 loading of 0.5 mol CO2/mol MEA solution and the procedure repeated that described for the corrosion system without inhibitor.
2.4.3 Corrosion System with Blended Inhibitors Imidazole/Morpholine, Dodecylamine/Morpholine and Sodium Molybdate/Morpholine.
Dodecylamine, sodium molybdate, and imidazole were blended with morpholine to see if the combination produced better inhibition.
The optimum concentrations of single inhibitors were used in blending and testing for its performance. The blended inhibitors were introduced into the corrosion cell containing 1 liter of 7 kmol/m3 MEA, CO2 loading of 0.5 mol CO2/mol MEA solution and the procedure was repeated.
A realistic system consisting of 7 kmol/m3 MEA, CO2 loading of 0.5 mol CO2/mol MEA solution with simulated flue gas stream of 204 ppm SO2 and 6% O2 at 353 K was used through out all experiments to determine the optimum concentration of the tested inhibitor. This condition is called an uninhibited system gave the corrosion rate of carbon steel about 211 mpy.
3.1 Corrosion System with Inhibitor
3.1.1 Imidazole
The experiments were performed by adding imidazole in concentrations from 0 to 5,000 ppm.
The corrosion rate was calculated based on equation (7) and presented as a function of imidazole concentration as shown in
While not wishing to be bound by theory it is believed that as imidazole is introduced into the system, it generally adsorbs over the metal surface forming a layer that functions as a barrier protecting the metal from the corrosion as shown in reaction (1). It is thought that imidazole promotes the formation of a chelate on a metal surface, by transferring electrons from its compound to the metal and forming a bond. In this way, the metal acts as an electrophile; and the nucleophile centers of imidazole molecule are normally the lone-pair of electrons on the N-1 atom, through the π-system of the imidazole ring, or through the unshared pair of electrons on the N-3 that are readily available for sharing, to form a bond. This phenomenon may be what is observed from the deviation of the current density at the anodic polarization curve as shown in
3.1.2 Dodecylamine
Dodecylamine was tested at concentrations of 0, 5, 10, and 25 ppm. Due to the limitation of dodecylamine solubility, higher concentrations of dodecylamine were not carried out.
The Tafel plot technique produces anodic and cathodic polarization curves. The corrosion current iCORR can be obtained by the intersection of extrapolating the linear portion of the curve to ECORR. The iCORR can be use to calculate corrosion rate by using equation (7). Generally, a higher iCORR leads to a higher corrosion rate. From the Tafel plots of dodecylamine, the corrosion rate can be calculated from iCORR obtained from the intersection of the linear portions of the polarization curve in both anode and cathode sites at ECORR.
While not wishing to be bound by theory it is believed that the corrosion inhibition shown by dodecylamine is due to adsorption of the substance on the metal surface via negatively charged centers on N atom. The hydrophobic part is believed to orientate toward the solution phase reducing access of the corrosive species to the metal surface. Suppression of the oxidation of iron at the anodic sites (reaction (1)) and the reduction of active agents at the cathodic site (reaction (2)-(6)) is believed to occur. This phenomenon may be observed by the deviation of the current density at both the anodic and cathodic polarization curve as shown in
3.1.3 Sodium Molybdate
The concentrations of sodium molybdate were varied from 10 to 10,000 ppm.
While not wishing to be bound by theory the inhibitive action of sodium molybdate could be explained on the basis that the inhibitor strongly adsorbed onto the metal surface. It is thought to form a highly insoluble film of sodium molybdate ions with iron ions which prevents the penetration of corrosive species, thereby decreasing the rate of corrosion.
Fe2++MoO42−FeMoO4 (9)
Moreover, when the concentration of inhibitor is high, the surplus sodium molybdate is thought to play a role in the inhibitive efficiency. Sodium molybdate can also react with H+ to form the complex ion of sodium molybdate. This ion may react with the steel to form a complex molecule that strongly adsorbs on the surface to further inhibit the corrosion.
[MoO42−]+H+→[MoO3(OH)]− (10)
The film which is formed between sodium molybdate ion and iron may also suppress the reduction of active agents; it reduces the current density at the cathodic site as shown in
3.1.4 Morpholine
The tested morpholine was spiked into the uninhibited system at concentrations of from 0 to 10,000 ppm.
The inhibition efficiency of morpholine was calculated to be 66-72% in the concentration range of 10-1,000 ppm as shown in
As shown in
SO2+H2OH++HSO3− (11)
HSO3−H++SO32− (12)
SO2+½O2+H2O2H++SO42− (13)
CO2+H2OH++HCO3− (14)
HCO3−H++CO32− (15)
RRNH+H+→RRNH2+ (16)
Morpholine is thought to control the amount of H+ generated by reaction (14). The elimination of H+ ion may also slightly reduce the oxidation of iron shown in reaction (1), which can be observed by a small reduction of the current density at the anode side as shown in
3.1.5 Commercial Inhibitor
Since this inhibitor is a commercial product, its chemical formula and structure are not known. Its mechanism is proposed based on the obtained Tafel plots from the experiment only. The polarization curve shows that commercial inhibitor seems to have a more significant suppression affect on anodic than cathodic sites. The commercial inhibitor appears to suppress the anode site or reaction (1) as compared the inhibited systems have a lower anodic current density than to the uninhibited system as shown in
3.2. Corrosion System with Blended Inhibitors
Combinations of inhibitors were also tested using morpholine (1,000 ppm) mixed with imidazole (1,000 ppm), dodecylamine (25 ppm), or sodium molybdate (1,000 ppm).
3.2.1 Imidazole/Morpholine
3.2.2 Dodecylamine/Morpholine
3.2.3 Sodium Molybdate/Morpholine
Based on the experimental results, dodecylamine, sodium molybdate, morpholine, can reduce corrosion. Blends of morpholine with dodecylamine, sodium molybdate, and imidazole can also reduce corrosion. Inhibition efficiency of each inhibitor also depends on its concentrations which can be concluded as follows.
This application is based on and claims domestic priority benefits under 35 USC §119(e) from U.S. Provisional Application Ser. No. 61/331,730 filed May 5, 2010, the entire content of which is expressly incorporated hereinto by reference.
Number | Date | Country | |
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61331730 | May 2010 | US |