(707f) Bio-Energy with Carbon Capture and Storage (BECCS): Opportunities for Efficiency Improvement | AIChE

(707f) Bio-Energy with Carbon Capture and Storage (BECCS): Opportunities for Efficiency Improvement

Authors 

Bui, M. - Presenter, Imperial College London
Fajardy, M., Imperial College London
Mac Dowell, N., Imperial College London
Bio-energy with carbon capture and storage (BECCS) will be a key mitigation technology in reducing atmospheric CO2 concentrations (Fuss et al., 2014; Fajardy and Mac Dowell, 2017; Mac Dowell and Fajardy, 2017). There are opportunities to improve efficiency and enhance commercial viability of BECCS. One approach is to recover waste heat from the power plant boiler system to supply thermal energy for the amine-based CO2 capture process (Harkin et al., 2009, 2010). The amount of heat available from the furnace exhaust gas is a function of adiabatic flame temperature (AFT), which in turn depends on fuel properties (Flagan and Seinfeld, 2012). Compared to higher quality coal, biomass tends to have lower heating value, lower ash and variable moisture content (5–60 wt% wet). The selection of a high quality biomass (e.g. low moisture and low ash) can have a positive impact on the combustion efficiency by increasing AFT (Sami et al., 2001), which in turn enhances heat recovery and energy efficiency (Bui et al., 2017a; Bui et al., 2017b). Additionally, biomass has lower sulphur and nitrogen content compared to coal, thus, co-firing can reduce the emissions of SOX and NOX (Spliethoff and Hein, 1998; Spliethoff et al., 2000).

This study evaluates the energy efficiency, recoverable heat and carbon intensity of a 500 MW pulverised fuel BECCS system for different biomass co-firing proportions and capture solvents. The modelling procedure used for this analysis is as follows:

  1. Selection of coal type (high and medium sulphur content), biomass type (wheat straw and clean wood chips), and CO2 capture solvents (MEA, Cansolv, “new solvent”).
  2. 500 MW ultra-supercritical power plant model: Calculates the fuel firing flow rate and net power output for different biomass co-firing proportions.
  3. Chemical equilibrium model of biomass and coal co-combustion: Determines the flue gas composition, flow rate, thermodynamic properties and adiabatic flame temperature (AFT).
  4. Heat recovery model: Calculations to determine the effect of flue gas heat recovery on the overall plant efficiency and carbon intensity.

The opportunities to improve BECCS energy efficiency include higher heat recovery (HR) and using high performance capture solvents, which can increase efficiency from 31%HHV (conventional MEA system) to 38%HHV (new solvent + HR). Significant reductions to SOX emissions can be obtained by increasing biomass co-firing proportion or using coals with low sulphur content. The level of NOX emissions depends on combustion conditions, and will increase with temperature. The low efficiency MEA system was more carbon negative on a per MWh basis compared to the high efficiency system. This was due to higher fuel consumption per MWh of electricity generated, thus, more CO2 is captured from the atmosphere. However, it is important to consider that the dispatch of higher efficiency systems is favoured due to their lower marginal cost of electricity generation. The annual carbon removal of a BECCS system depends on the efficiency and annual capacity of the power plant. Thus, there is a trade-off between efficiency and carbon intensity that needs to be considered when evaluating BECCS potential for climate mitigation.

References

  • Bui, M., Fajardy, M. & Dowell, N. M. (2017a). Thermodynamic evaluation of carbon negative power generation: Bio-energy CCS (BECCS). Energy Procedia, in press.
  • Bui, M., Fajardy, M. & Mac Dowell, N. (2017b). Bio-Energy with CCS (BECCS) performance evaluation: Efficiency enhancement and emissions reduction. Applied Energy, 195, 289–302.
  • Fajardy, M. & Mac Dowell, N. (2017). Can BECCS deliver sustainable and resource efficient negative emissions? Energy and Environmental Science, in press.
  • Flagan, R. C. & Seinfeld, J. H. (2012). Chapter 2 Combustion Fundamentals. Fundamentals of Air Pollution Engineering. New York, United States: Dover Publications Inc.
  • Fuss, S., Canadell, J. G., Peters, G. P., Tavoni, M., Andrew, R. M., Ciais, P., Jackson, R. B., Jones, C. D., Kraxner, F., Nakicenovic, N., Le Quere, C., Raupach, M. R., Sharifi, A., Smith, P. & Yamagata, Y. (2014). Betting on negative emissions. Nature Climate Change, 4 (10), 850–853.
  • Harkin, T., Hoadley, A. & Hooper, B. (2009). Process integration analysis of a brown coal-fired power station with CO2 capture and storage and lignite drying. Energy Procedia, 1 (1), 3817–3825.
  • Harkin, T., Hoadley, A. & Hooper, B. (2010). Reducing the energy penalty of CO2 capture and compression using pinch analysis. Journal of Cleaner Production, 18 (9), 857–866.
  • Mac Dowell, N. & Fajardy, M. (2017). Inefficient power generation as an optimal route to negative emissions via BECCS? Environmental Research Letters, in press.
  • Sami, M., Annamalai, K. & Wooldridge, M. (2001). Co-firing of coal and biomass fuel blends. Progress in Energy and Combustion Science, 27 (2), 171–214.
  • Spliethoff, H. & Hein, K. R. G. (1998). Effect of co-combustion of biomass on emissions in pulverized fuel furnaces. Fuel Processing Technology, 54 (1–3), 189–205.
  • Spliethoff, H., Scheurer, W. & Hein, K. R. G. (2000). Effect of co-combustion of sewage sludge and biomass on emissions and heavy metals behaviour. Process Safety and Environmental Protection, 78 (1), 33–39.

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