Microbial electrolysis carbon capture

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]

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.

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]