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CHARACTERIZATION OF FOAMING BEHAVIOR IN AMINE-BASED CO2 CAPTURE PLANTS

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Presentation on theme: "CHARACTERIZATION OF FOAMING BEHAVIOR IN AMINE-BASED CO2 CAPTURE PLANTS"— Presentation transcript:

1 CHARACTERIZATION OF FOAMING BEHAVIOR IN AMINE-BASED CO2 CAPTURE PLANTS
Research Review Meeting January 10 – 11, 2008 University of Texas at Austin, Texas BHURISA THITAKAMOL AND AMORNVADEE VEAWAB Faculty of Engineering, University of Regina CANADA

2 OUTLINE Introduction Objectives Experiment Results and discussions
1 Introduction Objectives Experiment Results and discussions Foam model Conclusions Future works Acknowledgements

3 INTRODUCTION Foaming problem in the CO2 absorption process
5 INTRODUCTION Foaming problem in the CO2 absorption process One of the most severe operational problems causing extra expenditures Occurring in both an absorber and a regenerator during plant start-up and operation Causing many adverse impacts on the plant operation Impacts based on plant experiences Excessive loss of alkanolamine solvents Premature flooding Reduction in plant throughput Off-spec products High alkanolamine carryover to downstream plants

4 INTRODUCTION Research on foaming problem:
6 INTRODUCTION 9 Research on foaming problem: For the CO2 absorption process in gas treating services Research group Alkanolamine type Contaminant Operating condition Pauley et al., 1989 MEA DEA MDEA Two formulated MDEA (with non specified additives) Formic acid Acetic acid Propionic acid Butyric acid Pentanoic acid n-hexanoic acid Octanoic acid Decanoic acid Dodecanoic acid Liquid hydrocarbon Atmospheric pressure McCarthy and Trebble, 1996 Methanol Corrosion inhibitor Antifoam agent Lubrication oil Organic acid Degradation product Suspended solid oC MPa Harruff, 1998 DGA 93oC up to 6.9 MPa Current foaming knowledge in the CO2 absorption process for a coal-fired power plant is limited: The application of the CO2 absorption process is relatively new for a coal-fired power plant. No reports of plant experiences and research work has published.

5 7 OBJECTIVES To obtain comprehensive foaming information from bench-scale experiments under well-simulated environments. To reveal the parametric effects as listed below on foaming Gas flow rate Solution volume CO2 loading Alkanolamine concentration Solution temperature Degradation product Corrosion inhibitor Alkanolamine type To establish the foam model to predict a steady-state pneumatic foam height (H) from the physical properties and operating conditions

6 EXPERIMENTS The pneumatic method modified from
8 EXPERIMENTS The pneumatic method modified from the standard ASTM D892 (ASTM, 1999) Recorded foam volume

7 (average steady foam volume)
9 EXPERIMENTS Recorded data: Foam volume (cm3) vs. Time (min) for each minute during the 25-minute blowing time o (average steady foam volume) Raw data ; o = Average foam volume (cm3) G = Gas flow rate (cm3/min) The foaminess coefficient () (Bikerman, 1973)

8 RESULTS AND DISCUSSIONS
10 RESULTS AND DISCUSSIONS EFFECT OF GAS FLOW RATE At 20 – 80 cm3/min, N2 flow rate ,  At 80 – 110 cm3/min, N2 flow rate ,  CONSTANT MEA MEA Working flow rate at 94 cm3/min (Test condition: 2.0 & 5.0 kmol/m3 MEA, 400 cm3 solution volume, 0.40 mol/mol CO2 loading and 40oC)

9 RESULTS AND DISCUSSIONS
11 RESULTS AND DISCUSSIONS EFFECT OF SOLUTION VOLUME At 200 – 400 cm3, solution volume ,  At 400 – 700 cm3, solution volume ,  CONSTANT Working Volume at 400 cm3 (Test condition: 2.0 kmol/m3 MEA, 94 cm3/min N2, 0.40 mol/mol CO2 loading and 40oC)

10 RESULTS AND DISCUSSIONS
12 RESULTS AND DISCUSSIONS EFFECT OF MONOETHANOLAMINE (MEA) CONCENTRATION Decreased surface tension Surface tension of CO2-unloaded aqueous MEA solution replotted from experimental data [Vázquez et al., 1997] MEA concentration ,  initially and then Increased bulk liquid viscosity Predicted viscosity of CO2-loaded aqueous MEA solutions from correlation [Weiland et al., 1998] (Test condition: MEA, 94 cm3/min N2, 400 cm3 solution volume, absorber top: 0.20 mol/mol CO2 loading/ 40oC & absorber bottom: 0.40 mol/mol CO2 loading/ 60oC)

11 RESULTS AND DISCUSSIONS
13 RESULTS AND DISCUSSIONS Decreased surface tension Surface tension of CO2-loaded aqueous MEA solution measured by Spinning Drop Interfacial Tensiometer Model 510 EFFECT OF CO2 LOADING CO2 loading ,  initially and then Increased bulk liquid viscosity Predicted viscosity of 5.0 kmol/m3 MEA solution from correlation [Weiland et al., 1998] (Test condition: 5.0 kmol/m3 MEA, 94 cm3/min N2, 400 cm3 solution volume and 40, 60 and 90oC)

12 RESULTS AND DISCUSSIONS Reduced bulk viscosity
14 RESULTS AND DISCUSSIONS EFFECT OF SOLUTION TEMPERATURE Solution temperature ,  0.20 mol CO2/mol MEA 0.40 mol CO2/mol MEA Reduced bulk viscosity Decreasing  (Test condition: 5.0 kmol/m3 MEA, 94 cm3/min N2, 400 cm3 solution volume and 0.20 & 0.40 mol/mol CO2 loading) Predicted viscosity of 5.0 kmol/m3 MEA solution from correlation [Weiland et al., 1998]

13 RESULTS AND DISCUSSIONS
15 RESULTS AND DISCUSSIONS EFFECT OF DEGRADATION PRODUCT Most degradation products added into aqueous MEA solution induce foam. Degradation product Average  (min) None 0.80  Ammonium thiosulfate 0.97  Glycolic acid 0.94  Sodium sulfite 0.92  Malonic acid 0.92  Oxalic acid 0.90  Sodium thiocyanate 0.90  Sodium chloride 0.89  Sodium thiosulfate 0.85  Bicine 0.85  Hydrochloric acid 0.83  Formic acid 0.83  Acetic acid 0.82  Sulfuric acid 0.77  (Test condition: 10,000 ppm of degradation product, 5.0 kmol/m3 MEA, 94 cm3/min N2, 400 cm3 solution volume, 0.40 mol/mol CO2 loading and 60oC)

14 RESULTS AND DISCUSSIONS
16 RESULTS AND DISCUSSIONS EFFECT OF CORROSION INHIBITOR Corrosion inhibitors added into aqueous MEA solution enhance . (Test condition: 1,000 ppm of corrosion inhibitor, 5.0 kmol/m3 MEA, 94 cm3/min N2, 400 cm3 solution volume, 0.40 mol/mol CO2 loading and 60oC) Surface tension of 5.0 kmol/m3 MEA solutions containing no CO2 loading at 25oC with/without 1000 ppm corrosion inhibitor (measured by KrÜss Tensiometer K100 using the Wihelmy plate’s principle)

15 RESULTS AND DISCUSSIONS
17 EFFECT OF ALKANOLAMINE TYPE Foam formation in MEA and MDEA but not in DEA and AMP solutions Only small amount of foam in AMP+MEA solution with the mixing ratio of 1:2 mol/mol Viscosity of CO2-unloaded aqueous alkanolamine solution at 60o replotted from experimental data Type of alkanolamine Average  MEA 0.85  0.004 DEA No foam MDEA 0.32  0.019 AMP MEA + MDEA (1:1) MEA + MDEA (2:1) MEA + MDEA (1:2) DEA + MDEA (1:1) DEA + MDEA (2:1) DEA + MDEA (1:2) MEA + AMP (1:1) MEA + AMP (1:2) MEA + AMP (2:1) 0.13  0.001 (Test condition: 4.0 kmol/m3 total alkanolamine conc., 94 cm3/min N2, 400 cm3 solution volume, 0.40 mol/mol CO2 loading, 60oC and mixing ratio of blended solution = 1:1, 2:1 and 1:2 (mole:mole)) Predicted viscosity of the CO2-unloaded aqueous blended alkanolamine solution (4.0 kmol/m3 total alkanolamine conc. and 60oC) from Grunberg and Nissan’s equation (Mandal et al., 2003))

16 FOAM MODEL: LITERATURE
18 FOAM MODEL: LITERATURE Researcher Foaming system Method Proposed equation Solution Gas Ito and Fruehan (1989) 28%Cao-42%SiO2-30%FeO slags Argon Dimensional analysis =  (, , ) Jiang and Fruehan (1991) 30%FeO (Cao/SiO2=1.25) and 0%FeO (Cao/SiO2=1.25) slags =  (, , , g) Zhang and Fruehan (1995) 40%Cao-40%SiO2-15%Al2O3-5%FeO slags =  (, , , g, Db) Ghag et al (1998) Water + 78 – 95% glycerinate +SDBS N2 1. =  (, , , g, Db);  is surface tension depression 2. =  (g, , Db, EM); EM is surface elasticity 3. =  (g, , Db, Eeff); Eeff is effective elasticity Pilon et al (2001) Results from other research works Dimensional analysis of the governing equation for the pneumatic foam layer proposed by (Bhakta and Ruckenstein, 1997) Pilon and Viskanta (2004) Dimensional analysis of the governing equation for the pneumatic foam layer proposed by (Bhakta and Ruckenstein, 1997) + Prediction of minimum superficial gas velocity (jm)

17 FOAM MODEL: DEVELOPMENT
19 Pilon et al (2001)

18 FOAM MODEL: RESULTS Foaming height equation
20 FOAM MODEL: RESULTS Foaming height equation where INSIGNIFICANT Pout = Pdispersion + Pfoam + P* when when when

19 21 FOAM MODEL: RESULTS

20 22 CONCLUSION Solution volume affects  when it is small. Increasing the solution volume to a certain quantity results in a constant foam volume or . An increase in gas flow rate decreases . The gas flow rate can lead to a constant  when increases to a certain value. Ranges of solution volume and gas flow rate that lead to a constant  were found for the CO2- aqueous alkanolamines. These ranges enable the generation of foam data that do not depend on solution volume, gas flow rate, pore size of gas disperser, and dimension of test cell. Variations in MEA concentration, CO2 loading and solution temperature affect . An increase in temperature decreases .  increases and then declines with increasing MEA concentration and CO2 loading. Most degradation products and corrosion inhibitors enhance . MEA, MDEA and AMP + MEA (1:2 mixing mole ratio) generate apparent foams FOAM MODEL is established to predict the steady-state pneumatic foam height from the physical properties and operating conditions and also to identify the important dimensionless numbers for a scaling-up hydrodynamic experiment. 31

21 FUTURE WORK FOAM MODEL HYDRODYNAMIC
23 FUTURE WORK FOAM MODEL Sensitivity analysis of input parameters on the predicted foam height. Model improvement by incorporating the minimum superficial gas velocity predicted based on the one-dimensional drift-flux model (Pilon and Viskanta, 2004) HYDRODYNAMIC Study the foaming behavior occurred in the packed absorber during absorption process based on dimensionless numbers in terms of the foaming tendency and the foam stability by measuring  and foam half-life, respectively. Investigate the effect of foaming on the hydrodynamic parameter s (e.g., pressure drop, liquid holdup and flooding point) of the packed CO2 absorption column based on dimensionless numbers.  FOAMING CHART

22 ACKNOWLEDGEMENT 24 Faculty of Graduate Studies and Research (FGSR), University of Regina Faculty of Engineering, University of Regina The Natural Sciences and Engineering Research Council (NSERC)


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