Photocatalytic defluorination of perfluorooctanoic acid by surface defective BiOCl: Fast microwave solvothermal synthesis and photocatalytic mechanisms
“…Degradation of all PFAS proceeded at similar rates in this reactor, as did the PFOA control experiment using no BOHP, which together indicates that photolysis was responsible and not photocatalysis. Unlike the lamps used in the immersion reactor experiments discussed above, those in the commercial reactor included 185 nm VUV emissions capable of directly photolyzing most PFAS. , Overall, F – recovery was significantly lower than that observed previously in the immersion reactor for PFOA, with PFHpA showing the lowest (23 ± 4%) and PFOA the highest (36 ± 2%), though no clear trend was observed. Since significant turbulence occurred where the recycled effluent and slurry reenter the influent reservoir (Figure C), air stripping is suspected to have resulted in loss of HF and other intermediate fluorinated compounds from the system.…”
Section: Resultsmentioning
confidence: 68%
“…Quenching of • OH by IPA markedly slowed PFOA degradation, with methanol and t -butanol having a similar effect (data not shown). While direct reaction of PFOA with • OH is known to be inefficient in homogeneous advanced oxidation, several works involving the reaction of PFOA at liquid–solid interfaces have reported similar results, including in photocatalytic and electrochemical systems. ,− Relating to the same behavior observed during PFOA degradation by a In 2 O 3 photocatalyst, Wu et al. proposed that • OH reacts with perfluoroalkyl radical intermediates formed by reaction of PFOA with h vb + (Reaction ) and thus accelerates the stepwise chain-shortening mineralization process .…”
Semiconductor photocatalysis is currently being explored as a treatment tool for wastewaters contaminated with poly-/ perfluoroalkyl substances (PFAS), such as groundwater impacted by aqueous film-forming foams. While numerous catalysts have been shown to degrade perfluorocarboxylic acids (PFCAs) such as PFOA, research thus far has been confined to bench-scale evaluations that offer little insight into the practical aspects and potential energy efficiency expected during full-scale application. Herein, we advanced such understanding using the recently discovered Bi 3 O(OH)(PO 4 ) 2 catalyst system (UV/ BOHP) by first elucidating the basic PFCA degradation mechanisms and behavior, followed by comparisons among different photoreactor designs. The BOHP suspension degraded PFCAs primarily through direct heterogeneous oxidation by valence band holes, and kinetics correlated positively with chain length. Degradation of PFCAs was further compared between stirred immersion photoreactors, bench-scale confined-flow high-intensity slurry photocatalytic reactors (CHISPRs), and a larger commercial CHISPR system. Complete degradation (>99%) of long-chain PFCAs was observed in the immersion reactors within 60 min, while the CHISPRs degraded all PFAS tested within 20 min; however, control tests revealed that direct photolysis by vacuum UV was the main driver in the CHISPRs. Despite their faster kinetics, the energy consumption (per order removal) of PFOA photolysis in the unmodified CHISPRs was significantly higher (51−124 kWh/m 3 ) compared to PFOA photocatalysis in the immersion reactors (25 ± 4 kWh/ m 3 ). Based on these findings, practical photoreactor design criteria were proposed which incorporate both photolysis and photocatalysis, and which have implications beyond just the UV/BOHP process.
“…Degradation of all PFAS proceeded at similar rates in this reactor, as did the PFOA control experiment using no BOHP, which together indicates that photolysis was responsible and not photocatalysis. Unlike the lamps used in the immersion reactor experiments discussed above, those in the commercial reactor included 185 nm VUV emissions capable of directly photolyzing most PFAS. , Overall, F – recovery was significantly lower than that observed previously in the immersion reactor for PFOA, with PFHpA showing the lowest (23 ± 4%) and PFOA the highest (36 ± 2%), though no clear trend was observed. Since significant turbulence occurred where the recycled effluent and slurry reenter the influent reservoir (Figure C), air stripping is suspected to have resulted in loss of HF and other intermediate fluorinated compounds from the system.…”
Section: Resultsmentioning
confidence: 68%
“…Quenching of • OH by IPA markedly slowed PFOA degradation, with methanol and t -butanol having a similar effect (data not shown). While direct reaction of PFOA with • OH is known to be inefficient in homogeneous advanced oxidation, several works involving the reaction of PFOA at liquid–solid interfaces have reported similar results, including in photocatalytic and electrochemical systems. ,− Relating to the same behavior observed during PFOA degradation by a In 2 O 3 photocatalyst, Wu et al. proposed that • OH reacts with perfluoroalkyl radical intermediates formed by reaction of PFOA with h vb + (Reaction ) and thus accelerates the stepwise chain-shortening mineralization process .…”
Semiconductor photocatalysis is currently being explored as a treatment tool for wastewaters contaminated with poly-/ perfluoroalkyl substances (PFAS), such as groundwater impacted by aqueous film-forming foams. While numerous catalysts have been shown to degrade perfluorocarboxylic acids (PFCAs) such as PFOA, research thus far has been confined to bench-scale evaluations that offer little insight into the practical aspects and potential energy efficiency expected during full-scale application. Herein, we advanced such understanding using the recently discovered Bi 3 O(OH)(PO 4 ) 2 catalyst system (UV/ BOHP) by first elucidating the basic PFCA degradation mechanisms and behavior, followed by comparisons among different photoreactor designs. The BOHP suspension degraded PFCAs primarily through direct heterogeneous oxidation by valence band holes, and kinetics correlated positively with chain length. Degradation of PFCAs was further compared between stirred immersion photoreactors, bench-scale confined-flow high-intensity slurry photocatalytic reactors (CHISPRs), and a larger commercial CHISPR system. Complete degradation (>99%) of long-chain PFCAs was observed in the immersion reactors within 60 min, while the CHISPRs degraded all PFAS tested within 20 min; however, control tests revealed that direct photolysis by vacuum UV was the main driver in the CHISPRs. Despite their faster kinetics, the energy consumption (per order removal) of PFOA photolysis in the unmodified CHISPRs was significantly higher (51−124 kWh/m 3 ) compared to PFOA photocatalysis in the immersion reactors (25 ± 4 kWh/ m 3 ). Based on these findings, practical photoreactor design criteria were proposed which incorporate both photolysis and photocatalysis, and which have implications beyond just the UV/BOHP process.
“…The decomposition of PFOA was initiated by direct hole oxidation, and the tight coordination of PFOA is essential for direct hole oxidation . Diffuse reflectance infrared Fourier transform spectroscopy (DRIFTS) is a useful technique for gaining insight into the mode of coordination between PFOA and semiconductor photocatalysts. , In situ DRIFTS was widely used to track the reaction intermediates and products to better understand reaction mechanisms. , …”
Section: Introductionmentioning
confidence: 99%
“…15 Diffuse reflectance infrared Fourier transform spectroscopy (DRIFTS) is a useful technique for gaining insight into the mode of coordination between PFOA and semiconductor photocatalysts. 16,17 In situ DRIFTS was widely used to track the reaction intermediates and products to better understand reaction mechanisms. 18,19 Previous studies demonstrate that the calcination temperature could significantly affect the photoelectrochemical performance of In 2 O 3 films by introducing different concentrations of oxygen vacancies.…”
In this study, four kinds of In 2 O 3 photocatalysts were prepared by a facile calcination process at different temperatures and used for the removal of perfluorooctanoic acid (PFOA) from contaminated water. Lower calcination temperatures induce higher oxygen vacancy concentrations and larger specific surface areas, thus improving the PFOA degradation performance of In 2 O 3 . In 2 O 3 prepared at lower temperatures of 300 °C (In 2 O 3 -300) and 400 °C (In 2 O 3 -400) demonstrates better catalytic performance, and 10 mg L −1 PFOA could be completely removed within 4 h, with a defluorination ratio of 35% over In 2 O 3 -300 and 39% over In 2 O 3 -400 in 8 h. Fe 3+ only slightly increased the defluorination ratio of PFOA over In 2 O 3 -400 to 43%. A defluorination ratio of ∼20% over In 2 O 3 -600 was obtained in 8 h, while when Fe 3+ was added to the photocatalytic systems, a higher defluorination ratio of ∼60% was obtained in the In 2 O 3 -600 system. Combining diffuse reflectance infrared Fourier transform spectroscopy (DRIFTS) and in situ DRIFTS to track the decomposition of PFOA, we speculated that Fe 3+ participated in the coordination between PFOA and In 2 O 3 -600, thus promoting the defluorination of PFOA.
“…A total 21 articles published since 2017 reporting on the solar and visible light-induced photocatalytic degradation of PFOA have been surveyed in this review (Figure ). The legendary photocatalyst, pristine-/modified-titanium dioxide (TiO 2 ), ,− and the photocorrosion resistant pristine-/modified-bismuth oxyhalide (BiOX) photocatalysts ,,,, equally share this investigation (5 publications each). The photocatalytic degradation of PFOA has been explored (4 publications) over photostable, modified indium oxide (In 2 O 3 ) photocatalysts. ,, Only a single article each on modified zinc oxide (ZnO) and bismuth oxide photocatalysts is reported.…”
Section: Present Status Of Photocatalytic
Degradation
Of Pfamentioning
Poly-and perfluoroalkyls (PFAs) are now designated as serious threats to the environment. More than 4700 PFAs, along with their precursors, show a high degree of persistence and long-range spreading in soils and waters causing recalcitrant bioaccumulation in plants, fish, birds, and mammals causing health hazards all along the food chain. Visible-light induced degradation of PFA in pure water using photocatalysts, a potentially sustainable advanced oxidation process, showed exciting results in laboratories for both complete and partial mineralization of these toxins. However, none of the methods and materials have been considered so far for upscaling toward practical applications due to several hard-to-resolve challenges. This Review provides a critical analysis of the recent advancements in photocatalytic remediation of aqueous PFA under visible light irradiation and addresses possible future directions to valorize some of the prospective methods and materials to practical applications.
scite is a Brooklyn-based organization that helps researchers better discover and understand research articles through Smart Citations–citations that display the context of the citation and describe whether the article provides supporting or contrasting evidence. scite is used by students and researchers from around the world and is funded in part by the National Science Foundation and the National Institute on Drug Abuse of the National Institutes of Health.