Nanosized titanium dioxide (TiO2) is a naturally existing
nanoscale semiconducting mineral, and its co-occurrence with microbes
may elicit differential environmental effects. In this study, the
impacts of TiO2 nanoparticles (NPs) on the reductive dissolution
of As(V) and Fe(III) from flooded arsenic-enriched soils were examined
under intermittent illumination and dark conditions. The amendment
with TiO2 NPs under intermittent illumination resulted
in the highest As/Fe reduction among all amendments. In the amendment
with TiO2 NPs, the maximum concentrations of Fe(II) derived
from intermittent illumination and dark treatments were nearly 2.1-
and 1.7-fold higher than the soils amended with acetate alone under
dark conditions (36.5 ± 4.5 mg/L), respectively, and nearly 1.6-
and 1.2-fold higher than the increased As(III) concentrations (8175.2
± 125.5 μg/L) detected under the same conditions. However,
the removal of total organic carbon derived from the amendment with
acetate-TiO2 NPs under intermittent illumination was only
0.8 times that of the amendment with acetate alone under dark conditions.
Because TiO2 NPs are highly responsive to sunlight, more
photoelectrons supplied from intermittently illuminated soils were
separated synchronously by accompanying them with the capture of photoholes
by humic/fulvic acids; thereafter, the photoelectrons participated
in As(V)/Fe(III) reduction. In addition, the electrical conductivities
of TiO2 NPs-supplemented soil particles were nearly 1.6-fold
higher than that of nonsupplemented samples, thereby enabling a long-distance
electron transfer. Moreover, the amendment with TiO2 NPs
with intermittent illumination resulted in an increase to the abundances
of several metal-reducing bacteria in the soil microbial community,
e.g., Bacillus, Thermincola, Pseudomonas, and Clostridium, correspondingly boosting the involved
microbial degradation of organic substrates to supply more bioelectrons
for As(V)/Fe(III) reduction. The findings have an important implication
on the understanding of the role of nanosized minerals in the biogeochemical
cycling of metal pollutants.
This study examined the role of intermittent illumination/dark conditions coupled with MnO 2-ammendments to regulate the mobility of As and Fe in flooded arsenic-enriched soils. Addition of MnO 2 particles with intermittent illumination led to a pronounced increase in the reductive-dissolution of Fe(III) and As(V) from flooded soils compared to a corresponding dark treatments. A higher MnO 2 dosage (0.10 vs 0.02 g) demonstrated a greater effect. Over a 49-day incubation, maximum Fe concentrations mobilized from the flooded soils amended with 0.10 and 0.02 g MnO 2 particles were 2.39 and 1.85-fold higher than for non-amended soils under dark conditions. The corresponding maximum amounts of mobilized As were at least 92 % and 65 % higher than for nonamended soils under dark conditions, respectively. Scavenging of excited holes by soil humic/fulvic compounds increased mineral photoelectron production and boosted Fe(III)/As(V) reduction in MnO 2-amended, illuminated soils. Additionally, MnO 2 amendments shifted soil microbial community structure by enriching metal-reducing bacteria (e.g., Anaeromyxobacter, Bacillus and Geobacter) and increasing c-type cytochrome production. This microbial diversity response to MnO 2 amendment facilitated direct contact extracellular electron transfer processes, which further enhanced Fe/As reduction. Subsequently, the mobility of released Fe(II) and As(III) was
The separation of vanadium (V) and molybdenum (VI) was studied by co-extraction with an aqueous two-phase system formed by PEG2000 + sodium sulfate + water and by selective stripping with another aqueous two-phase system formed by ammonium sulfate solution and PEG2000 phase loaded vanadium and molybdenum. The effect of aqueous pH, concentration of vanadium and molybdenum, temperature on the co-extraction and concentration of ammonium sulfate, temperature and phase ratio on selective stripping separation of vanadium and molybdenum was investigated. The experimental results on co-extraction of vanadium and molybdenum indicated that the co-extraction rate of both metals is sensitive to aqueous pH, and their extraction rate can achieve above 97.54% and 99.49%, respectively, when the pH value of aqueous solution is at 2.0, the molar ratio of vanadium to molybdenum is about 1.5, the concentration of PEG2000 is 20%, and the temperature is 313.15 K, respectively. The co-extraction rate of both metals decreases slightly with an increase in temperature from 313.15 to 343.15 K. The extraction isotherm and McCabe-Thiele method showed that two theoretical stages are needed when concentration of vanadium and molybdenum decreases from initial 12 g/L and 10 g/L to 0.1 g/L under the optimal conditions. The results on selective stripping of both metals from loaded PEG2000 phase to aqueous phase indicated that the stripping rate and precipitation rate of vanadium are evidently impacted by aqueous pH within 8.0 ~ 11.0 and then a little influenced by other parameters. The stripping rate of molybdenum is relatively lower than that of vanadium and is influenced by all kinds of stripping conditions. The stripping rate and precipitation rate of vanadium achieve 99.88% and 98.84%, respectively, and stripping rate of molybdenum achieves 81.99% under the optimal stripping conditions of O/A = 2:1, stripping temperature 343.15 K, (NH 4 ) 2 SO 4 (w/w) 40% and the pH of aqueous solution at 10.0.
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