9 research outputs found
Modular Advanced Oxidation Process Enabled by Cathodic Hydrogen Peroxide Production
Hydrogen
peroxide (H<sub>2</sub>O<sub>2</sub>) is frequently used
in combination with ultraviolet (UV) light to treat trace organic
contaminants in advanced oxidation processes (AOPs). In small-scale
applications, such as wellhead and point-of-entry water treatment
systems, the need to maintain a stock solution of concentrated H<sub>2</sub>O<sub>2</sub> increases the operational cost and complicates
the operation of AOPs. To avoid the need for replenishing a stock
solution of H<sub>2</sub>O<sub>2</sub>, a gas diffusion electrode
was used to generate low concentrations of H<sub>2</sub>O<sub>2</sub> directly in the water prior to its exposure to UV light. Following
the AOP, the solution was passed through an anodic chamber to lower
the solution pH and remove the residual H<sub>2</sub>O<sub>2</sub>. The effectiveness of the technology was evaluated using a suite
of trace contaminants that spanned a range of reactivity with UV light
and hydroxyl radical (HO<sup>•</sup>) in three different types
of source waters (i.e., simulated groundwater, simulated surface water,
and municipal wastewater effluent) as well as a sodium chloride solution.
Irrespective of the source water, the system produced enough H<sub>2</sub>O<sub>2</sub> to treat up to 120 L water d<sup>–1</sup>. The extent of transformation of trace organic contaminants was
affected by the current density and the concentrations of HO<sup>•</sup> scavengers in the source water. The electrical energy per order
(<i>E</i><sub>EO</sub>) ranged from 1 to 3 kWh m<sup>–3</sup>, with the UV lamp accounting for most of the energy consumption.
The gas diffusion electrode exhibited high efficiency for H<sub>2</sub>O<sub>2</sub> production over extended periods and did not show a
diminution in performance in any of the matrices
Concomitant Leaching and Electrochemical Extraction of Rare Earth Elements from Monazite
Rare earth elements (REEs) have become
increasingly important in
modern day technologies. Unfortunately, their recycling is currently
limited, and the conventional technologies for their extraction and
purification are exceedingly energy and chemical intensive. New sustainable
technologies for REE extraction from both primary and secondary resources
would be extremely beneficial. This research investigated a two-stage
recovery strategy focused on the recovery of neodymium (Nd) and lanthanum
(La) from monazite ore that combines microbially based leaching (using
citric acid and spent fungal supernatant) with electrochemical extraction.
Pretreating the phosphate-based monazite rock (via roasting) dramatically
increased the microbial REE leaching efficiency. Batch experiments
demonstrated the effective and continued leaching of REEs by recycled
citric acid, with up to 392 mg of Nd L<sup>–1</sup> and 281
mg of La L<sup>–1</sup> leached during seven consecutive 24
h cycles. Neodymium was
further extracted in the catholyte of a three-compartment electrochemical
system, with up to 880 mg of Nd L<sup>–1</sup> achieved within
4 days (at 40 A m<sup>–2</sup>). Meanwhile, the radioactive
element thorium and counterions phosphate and citrate were separated
effectively from the REEs in
the anolyte, favoring REE extraction and allowing sustainable reuse
of the leaching agent. This study shows a promising technology that
is suitable for primary ores and can further be optimized for secondary
resources
Transmission electron microscopy (TEM) images of thin sections of the five different bacterial species, loaded with platinum particles.
<p>The precipitation of platinum was induced by the presence of hydrogen gas. No Pt particles were observed during the recovery of cisplatin by <i>Bacillus toyonensis</i> and <i>Pseudomonas stutzeri</i>, while <i>Geobacter metallireducens</i> was not studied for this complex.</p
An overview of the platinum recovery efficiencies (%) at pH 2 is given; the Pt recovery was investigated with and without (sorption control) the addition of H<sub>2</sub>-gas.
<p>The platinum recovery was studied using five different bacterial species and five Pt-complexes (n = 1). All recoveries were measured after 48 h, except for: * 68 h, ** 107 h and *** 168 h, and **** 320 h. The chemical reduction was studied for all Pt-species using H<sub>2</sub>-gas.</p
The effect of the addition of Pt(II)Cl42- on the membrane integrity of different bacterial cells during platinum recovery as a function of time.
<p>Four different bacterial cultures were studied; <i>Shewanella oneidensis</i> MR-1, <i>Cupriavidus metallidurans</i> CH34, <i>Bacillus toyonensis</i> and <i>Pseudomonas stutzeri</i>. The recovery experiment was started at t<sub>0</sub> by the addition of 100 mg L<sup>-1</sup> Pt and H<sub>2</sub>-gas as electron donor. The pH was initially set at pH 2.0.</p
X-ray absorption near edge spectroscopy (XANES) spectra of biomass pellet samples after Pt(II)Cl42- recovery (100 mg L<sup>-1</sup> Pt; 50 mg L<sup>-1</sup> Pt in case of anaerobic <i>S</i>. <i>oneidensis</i>), by three bacterial species: <i>Geobacter metallireducens</i>, <i>Cupriavidus metallidurans</i> CH34 and <i>Shewanella oneidensis</i> MR-1.
<p>X-ray absorption near edge spectroscopy (XANES) spectra of biomass pellet samples after Pt(II)Cl42- recovery (100 mg L<sup>-1</sup> Pt; 50 mg L<sup>-1</sup> Pt in case of anaerobic <i>S</i>. <i>oneidensis</i>), by three bacterial species: <i>Geobacter metallireducens</i>, <i>Cupriavidus metallidurans</i> CH34 and <i>Shewanella oneidensis</i> MR-1.</p
X-ray absorption near edge spectroscopy (XANES) spectra of biomass pellet samples after Pt(IV)Cl62- recovery (100 mg L<sup>-1</sup> Pt; 50 mg L<sup>-1</sup> Pt in case of anaerobic <i>Shewanella</i>), by two bacterial species: <i>Geobacter metallireducens</i> and <i>Shewanella oneidensis</i> MR-1.
<p>X-ray absorption near edge spectroscopy (XANES) spectra of biomass pellet samples after Pt(IV)Cl62- recovery (100 mg L<sup>-1</sup> Pt; 50 mg L<sup>-1</sup> Pt in case of anaerobic <i>Shewanella</i>), by two bacterial species: <i>Geobacter metallireducens</i> and <i>Shewanella oneidensis</i> MR-1.</p
Biogenic Nanopalladium Based Remediation of Chlorinated Hydrocarbons in Marine Environments
Biogenic catalysts
have been studied over the last 10 years in
freshwater and soil environments, but neither their formation nor
their application has been explored in marine ecosystems. The objective
of this study was to develop a biogenic nanopalladium-based remediation
method for reducing chlorinated hydrocarbons from marine environments
by employing indigenous marine bacteria. Thirty facultative aerobic
marine strains were isolated from two contaminated sites, the Lagoon
of Mar Chica, Morocco, and Priolo Gargallo Syracuse, Italy. Eight
strains showed concurrent palladium precipitation and biohydrogen
production. X-ray diffraction and thin section transmission electron
microscopy analysis indicated the presence of metallic Pd nanoparticles
of various sizes (5–20 nm) formed either in the cytoplasm,
in the periplasmic space, or extracellularly. These biogenic catalysts
were used to dechlorinate trichloroethylene in simulated marine environments.
Complete dehalogenation of 20 mg L<sup>–1</sup> trichloroethylene
was achieved within 1 h using 50 mg L<sup>–1</sup> biogenic
nanopalladium. These biogenic nanoparticles are promising developments
for future marine bioremediation applications
Electrolytic Membrane Extraction Enables Production of Fine Chemicals from Biorefinery Sidestreams
Short-chain
carboxylates such as acetate are easily produced through
mixed culture fermentation of many biological waste streams, although
routinely digested to biogas and combusted rather than harvested.
We developed a pipeline to extract and upgrade short-chain carboxylates
to esters via membrane electrolysis and biphasic esterification. Carboxylate-rich
broths are electrolyzed in a cathodic chamber from which anions flux
across an anion exchange membrane into an anodic chamber, resulting
in a clean acid concentrate with neither solids nor biomass. Next,
the aqueous carboxylic acid concentrate reacts with added alcohol
in a water-excluding phase to generate volatile esters. In a batch
extraction, 96 ± 1.6% of the total acetate was extracted in 48
h from biorefinery thin stillage (5 g L<sup>–1</sup> acetate)
at 379 g m<sup>–2</sup> d<sup>–1</sup> (36% Coulombic
efficiency). With continuously regenerated thin stillage, the anolyte
was concentrated to 14 g/L acetic acid, and converted at 2.64 g (acetate)
L<sup>–1</sup> h<sup>–1</sup> in the first hour to ethyl
acetate by the addition of excess ethanol and heating to 70 °C,
with a final total conversion of 58 ± 3%. This processing pipeline
enables direct production of fine chemicals following undefined mixed
culture fermentation, embedding carbon in industrial chemicals rather
than returning them to the atmosphere as carbon dioxide