Microbial electrolysis carbon capture

Microbial electrolysis carbon capture (MECC) is a carbon capture technique using microbial electrolysis cells during wastewater treatment. MECC results in net negative carbon emission wastewater treatment by removal of carbon dioxide (CO2) during the treatment process in the form of calcite (CaCO3), and production of profitable H2 gas.

Anthropogenic carbon dioxide emissions contribute to significant regional climate change due to the compound's contribution to the greenhouse gas effect in the atmosphere. Most mitigation goals to remove CO2 from the atmosphere are based on high levels of CO2 produced by fossil fuel combustion as a basis for energy production. The use of fossil fuels emits CO2 and other toxic compounds such as SOx and NOx in the process of combustion. Economic growth is reliant on energy production for transportation and industrial production of goods and services, the amount of CO2 emitted is predicted to continue to increase in the foreseeable future.

Net emissions of greenhouse gases of anthropogenic actions

Wastewater processing reflects a small percentage of greenhouse gas emissions. Currently, wastewater treatment consumes "3% of total electricity within the U.S."[1] At least 12 trillion gallons of wastewater are treated in the United States alone per year, which contributes to 1.5% of global greenhouse gas emissions.[1] Microbial electrolysis carbon capture (MECC) is a process that contributes to sustainable energy practice in both private and public sectors. MECC takes advantage of properties inherent to wastewater, such as organic content, to remove carbon dioxide and produce calcite precipitate and hydrogen gas.

Background

Wastewater treatment plants are held accountable by The 2004 Greenhouse Gas Protocol Initiative for their emissions of greenhouse gases by the use of electricity to treat wastewater.[2] For example, energy is required for the aeration process that releases volatile compounds from the water, and also for the mixing and transportation of polluted and recycled fluid moving throughout the process.[2] The electricity generation process itself necessary for wastewater treatment produces CO2, CH4, and nitrous oxide.[2] The aerobic treatment step of the water releases N2O and CO2, similar to the particle settling step, and the activated sludge step releases both CO2 and methane.[2]

The activated sludge step in wastewater treatment releases compounds such as methane and CO2.

Microbes in wastewater have the potential to enhance mineralization of CO2.[1] Mineralization of CO2 into CaCO3 immobilizes CO2 which prevent leakages by stabilizing underground pressure and reducing permeability of the cap rock.[3] By Le Chatelier's principle, increasing Ca2+ availability and increasing pH will increase the rate of mineralization.[3] Negatively charged surfaces on microbes have a high affinity for cations such as Ca2+ and, though metabolic function, increase saturation of CO2 in solution.[1] In addition, bacterial ureolysis (hydrolysis of urea) increases pH of the solution.[3]

Technology of MECC using wastewater

The microbial electrolytic process uses wastewater as a source of charged ions and outputs hydrogen gas through the use of the microbial electrolysis cell.[1] The wastewater itself provides electrolytes and is used to dissolve minerals.[1] It is in the wastewater where reactions occur that bind CO2 molecules to make new substances.[1]

On the anode, microorganisms called exoelectrogens interact with organic compounds to split hydrogen and produce CO2.[1] The resulting electrons travel through the circuit to the cathode, where they reduce water, to produce H2 gas and OH− ions.[1] The increased cathode pH dissolves silicate minerals, releasing metal ions such as Ca2+. Protons (H+) produced at the anode act with these metal ions to capture and ultimately mineralize CO2 into carbonate.[1] Due to the high production of H2 gas, and the ability for the system to recycle up to 95% of the gas, the result is a gain of  57-63kJ/mol CO2 , or a gain of 63kJ per mol of CO2 captured.[1]

The CO2 sequestered and H2 produced with this method, as well as being "net energy positive" are specifically mentioned as the highlights of the process, as well as the opportunity to use recycled materials such as HCO3− produced by the MECC which is useful for water treatment plants.[1] The water leftover can be given to the external CO2 emissions plants (such as coal power).[1] An advantage of the MECC process over other alternative approaches like anaerobic digestion is that MECC works well at low temperatures, small-scale, and low COD concentrations.[4] The economics section describes current economic disadvantages of this process.

Economics of MECC

Microbial electrolytic carbon capture has yet to be implemented in present wastewater plants, therefore economic cost and benefits are current projections based on research of the technology rather than operational data. Lu et al. 2015 summarize the potential economic benefits of MECC use in their 2015 article in which they define the method of MECC.[1] Their results estimate a “$48 per ton CO2 mitigated”[1] net cost for MECC technology applied to wastewater plants. This estimation factors in the parasitic energy costs, operational costs and initial capital required to perform MECC, as well as potential cost offsets such as revenue due to water treatment, H2 production, and reduction in fossil fuel consumption for commercial manufacturing of H2 and treatment of wastewater.[1]

The projected net cost of $48 per ton of mitigated CO2 is lower than estimated costs for pulverized coal power plant post-combustion carbon capture absorption using MEA and geologic sequestration ($65/t-CO2),[5] which is currently the most prolific Carbon Capture and Sequestration (CCS) technique. The MECC cost projection is also lower than the cost of many other CCS technologies: the direct air CO2 capture methods (about $1000/t-CO2),[6] the Bio-Energy Carbon Capture and Storage (BECCS) technique ($60–250/t-CO2),[7] the abiotic electrolytic dissolution of silicate method ($86/t-CO2),[1][8] and the pulverized coal power plant carbon capture by absorption and membrane techniques ($70–270/t-CO2).[9] The economics of MECC approach to carbon capture will benefit from future investigation in optimizing design and materials used.[1] Further research is needed to predict the scope of costs and setbacks related to engineering and running a functional MECC system within current wastewater plants.[1]

Critics of MECC discuss inefficiencies of the process, installation, materials, and potential setbacks that may result in economic losses.[10] Although MECC is projected to be cheaper than other existing carbon capture techniques, it is considerably more expensive (on the order of 800 times more expensive) than present wastewater treatment technology and therefore faces a substantial barrier to implementation in public and private wastewater treatment plants.[10] Furthermore, the efficiency of Microbial Fuel Cell technology, which is analogous to the microbial system used within MECC, has been criticized for its unpredictability due to relying upon the chemical and nutrient content of varying wastewater, as well as the health of living microbes.[11][10] Inefficient MFCs lead to greater operation costs as cost offset fluctuates with departure from maximum efficiency of the system.[10]

References
  1. Lu, Lu; Huang, Zhe; Rau, Greg H.; Ren, Zhiyong Jason (2015-06-24). "Microbial Electrolytic Carbon Capture for Carbon Negative and Energy Positive Wastewater Treatment". Environmental Science & Technology. 49 (13): 8193–8201. doi:10.1021/acs.est.5b00875. ISSN 0013-936X. PMID 26076212.
  2. Snips, Laura (August–December 2009). "Quantifying the Greenhouse gas emissions of wastewater treatment plants".
  3. Mitchell, Andrew C.; Dideriksen, Knud; Spangler, Lee H.; Cunningham, Alfred B.; Gerlach, Robin (July 2010). "Microbially Enhanced Carbon Capture and Storage by Mineral-Trapping and Solubility-Trapping". Environmental Science & Technology. 44 (13): 5270–5276. doi:10.1021/es903270w. ISSN 0013-936X. PMID 20540571.
  4. Logan, Bruce E.; Call, Douglas; Cheng, Shaoan; Hamelers, Hubertus V. M.; Sleutels, Tom H. J. A.; Jeremiasse, Adriaan W.; Rozendal, René A. (2008-12-01). "Microbial Electrolysis Cells for High Yield Hydrogen Gas Production from Organic Matter". Environmental Science & Technology. 42 (23): 8630–8640. doi:10.1021/es801553z. ISSN 0013-936X. PMID 19192774.
  5. Smit, Berend; Reimer, Jeffrey A; Oldenburg, Curtis M; Bourg, Ian C (2013-06-18). Introduction to Carbon Capture and Sequestration. The Berkeley Lectures on Energy. IMPERIAL COLLEGE PRESS. doi:10.1142/p911. ISBN 9781783263271.
  6. House, K. Z.; Baclig, A. C.; Ranjan, M.; van Nierop, E. A.; Wilcox, J.; Herzog, H. J. Economic and energetic analysis of capturing CO2 from ambient air. Proc. Natl. Acad. Sci. U. S. A. 2011, 108 (51), 20428−20433.
  7. IPCC, "Intergovernmental Panel on Climate Change.Climate Change 2014: Mitigation of Climate Change. Contribution of Working Group III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change," [Edenhofer, O., R. Pichs-Madruga, Y. Sokona, E. Farahani, S. Kadner, K. Seyboth, A. Adler, I. Baum, S. Brunner, P. Eickemeier, B. Kriemann, J. Savolainen, S. Schlömer, C. von Stechow, T. Zwickel and J.C. Minx (eds.)], Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA, 2014.
  8. Rau, Greg H., et al. "Direct electrolytic dissolution of silicate minerals for air CO2 mitigation and carbon-negative H2 production." Proceedings of the National Academy of Sciences 110.25 (2013): 10095-10100.
  9. Intergovernmental Panel on Climate Change (2007), "Summary for Policymakers", Climate Change 2007, Cambridge University Press, pp. 1–24, doi:10.1017/cbo9780511546013.003, ISBN 9780511546013
  10. McCarty, Perry L., Jaeho Bae, and Jeonghwan Kim. "Domestic wastewater treatment as a net energy producer–can this be achieved?." (2011): 7100-7106.
  11. Logan, B. E. Microbial Fuel Cells; John Wiley & Sons: Hoboken, NJ, 2008.
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