TY - JOUR
T1 - Direct visualization of arsenic binding on green rust sulfate
AU - Perez, Jeffrey Paulo H.
AU - Freeman, Helen M.
AU - Brown, Andy P.
AU - van Genuchten, Case M.
AU - Dideriksen, Knud
AU - S'Ari, Mark
AU - Tobler, Dominique J.
AU - Benning, Liane G.
N1 - Funding Information:
This project has received funding from the European Union’s Horizon 2020 Marie Skłodowska-Curie Innovative Training Network Grant No. 675219. L.G.B. and H.M.F. acknowledge the financial support from the Helmholtz Recruiting Initiative (award number I-044-16-01). TEM access was possible through the Royal Society of Chemistry (RSC) Researcher Mobility Grant (Project No. RM1602-226) and Geo.X Travel Grant (Grant No. SO_087_GeoX) awarded to J.P.H.P., and the EPSRC grant EP/M028143/1 at the University of Leeds. C.M.v.G. acknowledges partial funding from an NWO Veni grant (Project No. 14400). Use of APS was supported by the U.S. Department of Energy, Office of Science, Office of Basic Energy Sciences, under Contract No. DE-AC02-06CH11357. D.J.T. and K.D. acknowledge financial support from the Danish Council for Independent Research (via DANSCATT) for travel to APS, and the assistance of Olaf Borkiewicz and Kevin A. Beyer during X-ray scattering measurements at APS beamline 11-ID-B, Argonne. The As K-edge EXAFS data were collected at the BM23 beamline at ESRF (Experiment No. EV-338), and the authors thank Sakura Pascarelli for assistance during beamtime.
Publisher Copyright:
© 2020 American Chemical Society.
PY - 2020/3/17
Y1 - 2020/3/17
N2 - "Green rust" (GR), a redox-active Fe(II)-Fe(III) layered double hydroxide, is a potential environmentally relevant mineral substrate for arsenic (As) sequestration in reduced, subsurface environments. GR phases have high As uptake capacities at circum-neutral pH conditions, but the exact interaction mechanism between the GR phases and As species is still poorly understood. Here, we documented the bonding and interaction mechanisms between GR sulfate and As species [As(III) and As(V)] under anoxic and circum-neutral pH conditions through scanning transmission electron microscopy (STEM) coupled with energy-dispersive X-ray (EDX) spectroscopy and combined it with synchrotron-based X-ray total scattering, pair distribution function (PDF) analysis, and As K-edge X-ray absorption spectroscopy (XAS). Our highly spatially resolved STEM-EDX data revealed that the preferred adsorption sites of both As(III) and As(V) are at GR crystal edges. Combining this data with differential PDF and XAS allowed us to conclude that As adsorption occurs primarily as bidentate binuclear (2C) inner-sphere surface complexes. In the As(III)-reacted GR sulfate, no secondary Fe-As phases were observed. However, authigenic parasymplesite (ferrous arsenate nanophase), exhibiting a threadlike morphology, formed in the As(V)-reacted GR sulfate and acts as an additional immobilization pathway for As(V) (∼87% of immobilized As). We demonstrate that only by combining high-resolution STEM imaging and EDX mapping with the bulk (differential) PDF and extended X-ray absorption fine structure (EXAFS) data can one truly determine the de facto As binding nature on GR surfaces. More importantly, these new insights into As-GR interaction mechanisms highlight the impact of GR phases on As sequestration in anoxic subsurface environments.
AB - "Green rust" (GR), a redox-active Fe(II)-Fe(III) layered double hydroxide, is a potential environmentally relevant mineral substrate for arsenic (As) sequestration in reduced, subsurface environments. GR phases have high As uptake capacities at circum-neutral pH conditions, but the exact interaction mechanism between the GR phases and As species is still poorly understood. Here, we documented the bonding and interaction mechanisms between GR sulfate and As species [As(III) and As(V)] under anoxic and circum-neutral pH conditions through scanning transmission electron microscopy (STEM) coupled with energy-dispersive X-ray (EDX) spectroscopy and combined it with synchrotron-based X-ray total scattering, pair distribution function (PDF) analysis, and As K-edge X-ray absorption spectroscopy (XAS). Our highly spatially resolved STEM-EDX data revealed that the preferred adsorption sites of both As(III) and As(V) are at GR crystal edges. Combining this data with differential PDF and XAS allowed us to conclude that As adsorption occurs primarily as bidentate binuclear (2C) inner-sphere surface complexes. In the As(III)-reacted GR sulfate, no secondary Fe-As phases were observed. However, authigenic parasymplesite (ferrous arsenate nanophase), exhibiting a threadlike morphology, formed in the As(V)-reacted GR sulfate and acts as an additional immobilization pathway for As(V) (∼87% of immobilized As). We demonstrate that only by combining high-resolution STEM imaging and EDX mapping with the bulk (differential) PDF and extended X-ray absorption fine structure (EXAFS) data can one truly determine the de facto As binding nature on GR surfaces. More importantly, these new insights into As-GR interaction mechanisms highlight the impact of GR phases on As sequestration in anoxic subsurface environments.
UR - http://www.scopus.com/inward/record.url?scp=85082145825&partnerID=8YFLogxK
U2 - 10.1021/acs.est.9b07092
DO - 10.1021/acs.est.9b07092
M3 - Article
C2 - 32078305
AN - SCOPUS:85082145825
SN - 0013-936X
VL - 54
SP - 3297
EP - 3305
JO - Environmental Science and Technology
JF - Environmental Science and Technology
IS - 6
ER -