4 research outputs found
Characterizing the Impacts of Deposition Techniques on the Performance of MnO<sub>2</sub> Cathodes for Sodium Electrosorption in Hybrid Capacitive Deionization
Capacitive deionization (CDI) is
currently limited by poor ion-selectivity
and low salt adsorption capacity of porous carbon electrodes. To enhance
selectivity and capacity via sodium insertion reactions, carbon aerogel
electrodes were modified by depositing amorphous manganese dioxide
layers via cyclic voltammetry (CV) and electroless deposition (ED).
MnO<sub>2</sub>-coated electrodes were evaluated in a hybrid capacitive
deionization system to understand the relationship between oxide coating
morphology, electrode capacitance, and sodium removal efficacy. Both
deposition techniques increased electrode capacitance, but only ED
electrodes improved desalination performance over bare aerogels. SEM
imaging revealed ED deposition distributed MnO<sub>2</sub> throughout
the aerogel, while CV deposition created a discrete crust, indicating
that CV electrodes were limited by diffusion. Sodium adsorption capacity
of ED electrodes increased with MnO<sub>2</sub> mass deposition, reaching
a maximum of 0.77 mmol-Na<sup>+</sup> per gram of cathode (2.29 mmol-Na<sup>+</sup> g-MnO<sub>2</sub><sup>–1</sup>), and peak charge efficiency
of 0.95. The presence of MnO<sub>2</sub> also positively shifted the
electrode potential window of sodium removal, reducing parasitic oxygen
reduction and inverting the desalination cycle so that energy discharge
coincides with salt removal (1.96 kg-NaCl kWh<sup>–1</sup>).
These results highlight the importance of deposition technique in
improving desalination with MnO<sub>2</sub>-coated electrodes
Extracellular Palladium Nanoparticle Production using Geobacter sulfurreducens
Sustainable
methods are needed to recycle precious metals and synthesize
catalytic nanoparticles. Palladium nanoparticles can be produced via
microbial reduction of soluble PdÂ(II) to Pd(0), but in previous tests
using dissimilatory metal reducing bacteria (DMRB), the nanoparticles
were closely associated with the cells, occupying potential reductive
sites and eliminating the potential for cell reuse. The DMRB Geobacter sulfurreducens was shown here to reduce
soluble PdÂ(II) to Pd(0) nanoparticles primarily outside the cell,
reducing the toxicity of metal ions, and allowing nanoparticle recovery
without cell destruction that has previously been observed using other
microorganisms. Cultures reduced 50 ± 3 mg/L PdÂ(II) with 1% hydrogen
gas (v/v headspace) in 6 h incubation tests [100 mg/L PdÂ(II) initially],
compared to 8 ± 3 mg/L (10 mM acetate) without H<sub>2</sub>.
Acetate was ineffective as an electron donor for palladium removal
in the presence or absence of fumarate as an electron acceptor. TEM
imaging verified that Pd(0) nanoparticles were predominantly in the
EPS surrounding cells in H<sub>2</sub>-fed cultures, with only a small
number of particles visible inside the cell. Separation of the cells
and EPS by centrifugation allowed reuse of the cell suspensions and
effective nanoparticle recovery. These results demonstrate effective
palladium recovery and nanoparticle production using G. sulfurreducens cell suspensions and renewable
substrates such as H<sub>2</sub> gas
Amplifying Progress toward Multiple Development Goals through Resource Recovery from Sanitation
The United Nations’
Sustainable Development Goals (SDGs)
recognize that current sanitation gaps must be closed to better serve
those without access to safely managed systems (Target 6.2: universal
sanitation coverage) and those connected to sewers without wastewater
treatment (Target 6.3: halving the proportion of untreated wastewater).
Beyond mitigating environmental and health concerns, implementing
resource recovery sanitation systems could simultaneously improve
the availability of agricultural nutrients (SDG 2) and household energy
(SDG 7). This study estimates the potential for global, regional,
and country-level resource recovery to impact nutrient and household
electricity use through 2030. We distinguish impacts from newly installed
sanitation systems (to achieve universal coverage), newly treated
wastewater systems (to halve the proportion of untreated wastewater),
and existing system replacement, while also considering urban and
rural disparities and spatial colocation of nutrients with agricultural
needs. This work points toward country-specific strategies for deriving
the greatest benefit from sanitation investments while also identifying
overarching trends to guide international research efforts. Globally,
potential nutrient gains are an order of magnitude larger than electricity
(a small fraction of total energy), and considerable impacts are possible
in the least-developed countries, six of which could double or offset
all projected nutrient and electricity use through newly installed
sanitation systems
Hydrogen Generation in Microbial Reverse-Electrodialysis Electrolysis Cells Using a Heat-Regenerated Salt Solution
Hydrogen gas can be electrochemically produced in microbial
reverse-electrodialysis
electrolysis cells (MRECs) using current derived from organic matter
and salinity-gradient energy such as river water and seawater solutions.
Here, it is shown that ammonium bicarbonate salts, which can be regenerated
using low-temperature waste heat, can also produce sufficient voltage
for hydrogen gas generation in an MREC. The maximum hydrogen production
rate was 1.6 m<sup>3</sup> H<sub>2</sub>/m<sup>3</sup>·d, with
a hydrogen yield of 3.4 mol H<sub>2</sub>/mol acetate at a salinity
ratio of infinite. Energy recovery was 10% based on total energy applied
with an energy efficiency of 22% based on the consumed energy in the
reactor. The cathode overpotential was dependent on the catholyte
(sodium bicarbonate) concentration, but not the salinity ratio, indicating
high catholyte conductivity was essential for maximizing hydrogen
production rates. The direction of the HC and LC flows (co- or counter-current)
did not affect performance in terms of hydrogen gas volume, production
rates, or stack voltages. These results show that the MREC can be
successfully operated using ammonium bicarbonate salts that can be
regenerated using conventional distillation technologies and waste
heat making the MREC a useful method for hydrogen gas production from
wastes