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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.    2023, Vol. 17 Issue (9) : 115    https://doi.org/10.1007/s11783-023-1715-z
RESEARCH ARTICLE
Enhancement of extracellular Cr(VI) reduction for anammox recovery using hydrazine: performance, pathways, and mechanism
Caiyan Qu1,2, Lushan Li1,2, Fan Feng1,2, Kainian Jiang3, Xing Wu1, Muchuan Qin1, Jia Tang1, Xi Tang1,2, Ruiyang Xiao1,2, Di Wu4, Chongjian Tang1,2()
1. School of Metallurgy and Environment, Central South University, Changsha 410083, China
2. Chinese National Engineering Research Center for Control & Treatment of Heavy Metal Pollution, Changsha 410083, China
3. Yongzhou Environmental Monitoring Station, Yongzhou 425000, China
4. Ghent University Global Campus, Incheon, Republic of Korea; Department of Green Chemistry and Technology, Ghent University, and Centre for Advanced Process Technology for Urban Resource Recovery (CAPTURE), Ghent 9000, Belgium
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Abstract

● N2H4 addition enhanced and recovered anammox performance under Cr(VI) stress.

● N2H4 accelerated electron transfer of Cr(VI) reduction for detoxification.

● N2H4 enhanced anammox metabolism for activity recovery from Cr(VI) inhibition.

● Extracellular Cr(VI) reduction to less toxic Cr(III) was the dominant mechanism.

The hexavalent chromium (Cr(VI)) would frequently impose inhibition to anaerobic ammonium oxidation (anammox) process, hindering the efficiency of nitrogen removal in wastewater treatment. Hydrazine (N2H4), which is an intermediate product of anammox, participates in intracellular metabolism and extracellular Cr(VI) reduction. However, the roles of N2H4-induced intracellular metabolism and extracellular reduction in nitrogen removal under Cr(VI) stress remain unclear. The addition of 3.67 mg/L of N2H4 increased the anammox activity by 17%. As an intermediate, N2H4 enhanced anammox metabolism by increasing the heme c content and electron transfer system activity. As a reductant, N2H4 accelerated the reduction of c-Cyts-mediated extracellular Cr(VI) to the less toxic Cr(III). Extracellular Cr(III) accounts for 74% of the total Cr in a Cr(VI)-stressed anammox consortia. These findings highlight that N2H4-induced extracellular Cr(VI) reduction is the dominant mechanism for the survival of anammox consortia. We also found that N2H4 increased the production of extracellular polymeric substances to sequester excessive Cr(VI) and produced Cr(III). Taken together, the study findings suggest a potential strategy for enhancing nitrogen removal from ammonium-rich wastewater contaminated with Cr(VI).

Keywords Extracellular Cr(VI) reduction      Electron transfer      Anammox      Hydrazine      Cr(VI) inhibition     
Corresponding Author(s): Chongjian Tang   
Issue Date: 17 April 2023
 Cite this article:   
Caiyan Qu,Lushan Li,Fan Feng, et al. Enhancement of extracellular Cr(VI) reduction for anammox recovery using hydrazine: performance, pathways, and mechanism[J]. Front. Environ. Sci. Eng., 2023, 17(9): 115.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-023-1715-z
https://academic.hep.com.cn/fese/EN/Y2023/V17/I9/115
Scenario a)Group b)TypeBiomassN2H4 dosage (mg/L)Cr(VI) dosage (mg/L)
Under Cr(VI) exposurew/o N2H4BioticAnammox7.5
w/ N2H4BioticAnammox3.677.5
After Cr(VI) inhibition c)R-w/o N2H4BioticAnammox
R-w/ N2H4BioticAnammox1.75
Demonstration of Cr(VI) reductionCr(VI) + sludgeBioticAnammox7.5
Cr(VI) + N2H4Abiotic3.677.5
Cr(VI) + N2H4 + sludgeBioticAnammox3.677.5
Tab.1  Experimental scenarios with Cr(VI) or N2H4 addition
Fig.1  Effects of N2H4 on nitrogen removal under Cr(VI) exposure and after Cr(VI) inhibition. (a) The total nitrogen (TN) degradation curves. (b) The specific anammox activity (SAA) and TN removal efficiency under Cr(VI) exposure and after Cr(VI) inhibition.
Fig.2  Effect of N2H4 on Cr(VI) reduction. (a) Mass balance calculations for total Cr in the effluent and sludge collected from the biotic test (Cr(VI) + N2H4 + sludge), abiotic test (Cr(VI) + N2H4), and biotic control (Cr(VI) + sludge). The proportion of reduced Cr(III) in the total Cr concentrations was further calculated to indicate the Cr(VI) reduction efficiency (data labels in white). (b) Intracellular and absorbed Cr(III) concentrations in the sludge. HPLC-ICP-MS chromatograms for Cr speciation in the effluent (c), and intracellular and absorbed (d) solutions collected from the biotic test.
Fig.3  Effects of N2H4 on the electron transfer system of the anammox consortia under Cr(VI) exposure and after Cr(VI) inhibition. (a) Electron transfer system activity (ETSA). (b) Heme c content. (c)–(d) UV-visible spectroscopy profiles of c-Cyts in the EPS and extracted cell solutions.
w/o N2H4w/ N2H4R-w/o N2H4R-w/ N2H4
EPS20.523.425.116.5
Cell34.931.225.840.4
Tab.2  Area analysis of the absorption peak at 410 nm in the UV-Vis spectra of the cell and EPS solutions extracted from the anammox sludge using four different treatments
Fig.4  Effects of N2H4 on extracellular polymeric substance (EPS) production by the anammox consortia under Cr(VI) exposure and after Cr(VI) inhibition. (a) EPS contents normalized to the respective sample biomass. (b) Distribution of the fluorescence regional integration in the EEM fluorescence spectra of EPS (Region I: aromatic protein I, Region II: aromatic protein II, Region III: fulvic acid-like, Region IV: soluble microbial byproduct-like, Region V: humic acid-like). The data labels on the pie charts represent the proportions of Regions I, IV, and V.
Fig.5  The underlying mechanisms through which hydrazine (N2H4) addition accelerated the electron transfer of anammox metabolism and extracellular Cr(VI) reduction to alleviate Cr(VI) inhibition. The red or white vertical arrows indicate increases in the electron transfer system activity (ETSA), heme c content, and c-Cyts concentration in the quantitative analysis. Moreover, N2H4 addition increased EPS production through c-di-GMP regulation to extracellularly sequester Cr(VI) or the produced Cr(III).
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