Abstract
An aluminum (Al)-based electrocoagulation (EC) system can effectively remove dissolved silica and hardness in groundwater. The effectiveness of Al-EC in terms of pollutant removal, Faradaic efficiency, and energy consumption depends on the interfacial electrolysis or passivation of the electrode in water. Thus, understanding the electrolysis reaction at the liquid/electrode interface during operation is important for sustainable EC deployment. A continuous flow-through Al-EC system was tested with various groundwater simulants, i.e., chloride (Cl-)-based, sulfate (SO42-)-based, and mixed solutions. High pollutant removal with low energy consumption was observed in Cl--based groundwater treatment, while low pollutant removal with high energy consumption was observed in SO42--based groundwater. For example, the required energy per unit mass of Al dosing in SO42--based groundwater is three times higher than that in Cl--based groundwater at 10 mA/cm2. However, increasing the Cl- concentration significantly reduces this energy demand. In SO42--based groundwater, the silicate removal efficiency drops from 85.1% to 24.0% compared to that for Cl--based groundwater, while Mg2+ and Ca2+ removal efficiencies decrease to 0.6% from 15.8% and 5.7% from 44.8%, respectively. To better understand this EC performance, we used in situ neutron reflectometry (NR) to examine the interfacial dynamics of Al dissolution and passivation at a 100 nm scale occurring on the surface of the sacrificial Al electrodes during EC. Ex situ X-ray reflectometry (XRR) was also used to support the in situ NR results. Both NR and XRR results revealed that Al dissolution is influenced by the presence of Cl- in the simulants, while a passivating layer forms on the electrode in a SO42--based solution. In the Cl--based solution, anodic Al dissolution occurred locally and inhomogeneously across the surface of the Al anode film, resulting in a localized thickness reduction over time. In the SO42--based solution, no apparent dissolution of the Al anode was identified. Instead, Al underwent oxidation, forming an amorphous Al2O3 surface layer within the Al electrode film that increased in thickness over time. In the mixed solution, both anodic Al dissolution and surface Al2O3 layer formation occurred, indicating that Al dissolution and surface Al2O3 layer formation are attributable to the Cl- and SO42- ions, respectively.
Original language | English |
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Pages (from-to) | 25996-26012 |
Number of pages | 17 |
Journal | ACS Applied Materials and Interfaces |
Volume | 17 |
Issue number | 17 |
DOIs | |
State | Published - Apr 30 2025 |
Funding
This work was supported by the National Alliance for Water Innovation (NAWI), through funding from the U.S. Department of Energy (DOE), Office of Energy Efficiency and Renewable Energy Office, Advanced Materials and Manufacturing Technologies Office under Funding Opportunity Announcement DE-FOA-0001905. SEM and X-ray reflectivity measurements were conducted at the Center for Nanophase Materials Sciences (CNMS) under the CNMS user program, and neutron reflectivity measurements were conducted at the Liquids Reflectometer beamline (BL-4B), Spallation Neutron Source (SNS), Oak Ridge National Laboratory. CNMS and SNS are the DOE Office of Science User Facilities. The authors are grateful to WaterTectonics for providing the flow-through EC reactor.
Keywords
- X-ray reflectometry
- aluminum dissolution and passivation
- electrocoagulation
- groundwater treatment
- in situ neutron reflectometry