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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

Postal Subscription Code 80-973

2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2021, Vol. 15 Issue (6) : 112    https://doi.org/10.1007/s11783-021-1399-1
RESEARCH ARTICLE
Effect of current density on groundwater arsenite removal performance using air cathode electrocoagulation
Yanxiao Si1,2, Fang Zhang2(), Hong Chen3, Guanghe Li1, Haichuan Zhang1, Dun Liu1
1. School of Environment and State Key Joint Laboratory of Environment Simulation and Pollution Control, Tsinghua University, Beijing 100084, China
2. Surface engineering division, Sinopec Petroleum Exploration and Production Research Institute, Beijing 100083, China
3. School of Energy and Environmental Engineering, University of Science and Technology Beijing, Beijing 100083, China
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Abstract

• With the same charge, current density had little effect on As(III) removal in ACEC.

• ACEC had the lowest energy consumption compared with EC/O2 or EC/N2.

• There was a trade-off relationship between energy consumption and removal time.

• The ·OH concentration in ACEC was 1.5 times of that in the EC/O2 system.

Naturally occurring arsenic enrichment in groundwater poses a huge threat to human health. Air cathode electrocoagulation (ACEC) has recently been proposed to enhance As(III) oxidation and lower energy consumption. In this study, ACEC, EC/O2 and EC/N2 were evaluated with different current densities from 1 to 8 mA/cm2 to investigate the effect on As(III) removal in different redox environments. Current density had no appreciable effect on arsenic removal efficiency given the same charge in ACEC because the concentration ratio of Fe/H2O2 under different current densities remained stable. However, in EC/O2 and EC/N2, As(III) removal was inhibited at higher current densities (4–8 mA/cm2), likely because more Fe(II) competed with As(III) for the oxidant, leading to less effective oxidation of As(III). In all EC systems, the ·OH units generated per power consumption reached the highest value at the lowest current density. Compared with other EC systems, the ACEC system showed lower energy consumption at all current densities due to the low energy consumption of the electrode reaction and more free radical generation. A lower current density saved more energy at the expense of time, showing the trade-off relationship between energy consumption and removal time. The operation costs for As(III) removal under optimal conditions were calculated as 0.028 $/m3 for ACEC, 0.030 $/m3 for EC/O2, and 0.085 $/m3 for EC/N2

Keywords Electrocoagulation      Air cathode      Arsenic      Current density      Energy consumption     
Corresponding Author(s): Fang Zhang   
Issue Date: 08 March 2021
 Cite this article:   
Yanxiao Si,Fang Zhang,Hong Chen, et al. Effect of current density on groundwater arsenite removal performance using air cathode electrocoagulation[J]. Front. Environ. Sci. Eng., 2021, 15(6): 112.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-021-1399-1
https://academic.hep.com.cn/fese/EN/Y2021/V15/I6/112
Fig.1  The schematic of experimental setup for (a) ACEC system, (b) EC/O2 system, (c) EC/N2 system.
Fig.2  Removal of As(III) (-log(CAs(III)/C0)) as a function of charge under different current densities in (a) ACEC, (b) EC/O2 and (c) EC/N2 systems. (98% As(III) removal indicated the residual As(III) concentration is 10 mg/L).
Fig.3  Effect of charge on ·OH generation under different current densities in (a) ACEC, (b) EC/O2 and (c) EC/N2 system, and (d) the ·OH production rate of different systems at the end of 1 h, and the negative of PR value means the system was in power–producing mode.
Fig.4   Correlation between As(Tot) removal (–log(CAs(Tot)/C0)) and the removal energy consumption per order (Wh/log·m3) at different current densities in (a) ACEC, (b) EC/N2, (c) EC/O2. (–log(C/C0)) is –1.7 indicated the residual As(Tot) concentration fulfill the WHO standard (10 μg/L).
Fig.5  Calculated As(Tot) removal time (min) to achieve WHO standards and the corresponding removal energy consumption (Wh/m3). for 1 mA/cm2, for 2 mA/cm2, for 4 mA/cm2, and for 8 mA/cm2.

(The EC/N2 could only achieve acceptable As removal at the current density of 2 mA/cm2 with an energy consumption 50.3 Wh/m3).

Electrode type Contaminants type Concentration Current density range (A/m2) Optimum current density
(A/m2)
Corresponding removal time
(min)
Removal
(%)
The least EEO or EEC Ref.
Fe and Fe As(III) 150 mg/L 1.75–7.5 2.5 12.5 95.3 12.5 Wh/log·m3 Kobya et al., 2011
Fe and Fe As(III) 50 mg/L 5.4–10.7 5.4 30 99.5 143.4 Wh/log·m3 Can et al., 2014
Fe and Fe As(III) 500 mg/L 10–80 10 15.5 98 Produced of 2.6 Wh/log·m3 This study
Fe and air cathode As(III) 500 mg/L 10–80 10 30.4 97.8 3.3 Wh/log·m3 This study
Al and Al Microalgae 3.63 × 1010 cells/L 22.2–66.7 22.2 7 98 58.3 Wh/log·m3 Shi et al., 2017
Al and Al phenol 50 mg/L 64–236 64 120 84 0.061
kWh/g COD
Abdelwahab et al., 2009
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