Microbial extracellular polymeric substances (EPS) with redox functional groups play a vital role in the bioconversion of pollutants, which can affect their reactivity toward diverse environmental pollutants. However, the redox interactions between different EPS and pollutants have not been addressed till date due to the absence of essential analytical methodologies. In this study, researchers from the University of Science and Technology, China used BI-4500 SPR with the EC-DualFlowTM analysis module to investigate the interactions between EPS and an aromatic pollutant named p-nitrophenol (PNP) by simultaneously monitoring the electrochemical reaction and their binding kinetics.1

Figure 1: The schematic diagram of the developed EC-SPR system.

Surface plasmon resonance (SPR) is a real-time, label-free, and concise method for probing biomolecular binding events and their kinetics.By combining electrochemical (EC) technology with SPR, the electrochemical interface process can be thoroughly explored.3 When an electrochemical reaction occurs, the thickness of the gold film changes which triggers variations in the SPR resonance angle (refractive index), and is recorded by the detector (Figure 1).4 In this study, the  EC SPR system served as a powerful tool to investigate the interactions between EPS at various redox states and an organic pollutant PNP by simultaneously monitoring the electrochemical reaction and the binding kinetics.

Figure 2: a) SPR sensorgrams  and  b) Nyquist plots of the interaction between EPS and PNP.

Table 1 presents the binding parameters (ka, kd , and KA) for various redox states of  EPS. The binding affinity of EPS to PNP is related to the redox states of EPS, with this order of EPSred > EPSraw > EPSox.

Binding  ParametersEPSredEPSrawEPSox
ka (L/g/s)8.741 × 10− 36.573 × 10− 44.836 × 10− 4
kd (1/s)2.753 × 10− 42.674 × 10− 44.465 × 10− 4
KA (L/g)31.752.4581.083
Rct (ohm)1.319 × 1051.978 × 1052.547 × 105

EPS reduced PNP to p-aminophenol by donating electrons, and the reductive process depended on the redox states of EPS, determined by their electron donating capacity. The binding rate of EPSred was significantly higher than that of EPSraw and EPSox, while the dissociation rate of the three forms was similar (Figure 2a). The association signal of EPSred with PNP increased to reach equilibrium rapidly, resulting in ka and KA values of 8.741 × 10− 3 Liters per gram per second (L/g/s) and 31.75 Liters per gram (L/g), which were ten times higher than those of EPSraw and EPSox. The equilibrium affinity constant (KA) for the binding reaction mentioned in this paper is calculated by dividing ka by kd. In the Nyquist plot in (Figure 2b) of the impedance spectrum, the charge transfer resistance (Rct) value was associated with the diameter of the semicircle observed at higher frequencies. EPSred showed the lowest charge transfer resistance, indicating that the redox re-action is more readily occurring between them. Both EPSred and EPSraw transfer electrons to the nitro group in PNP, resulting in the trans-formation of the nitro group to amino group. On the contrary, EPSox exhibited the highest Rct value indicating the lack of electron transfer to PNP. By employing electrochemical SPR experiments, this study clarified the difference in the reduction of PNP by EPS at different redox states and showed that the reduced state of EPS has the maximum ability to transfer electrons to PNP. This work contributes to a comprehensive understanding of the critical role of EPS redox property in the conversion of refractory pollutants like PNP in biological wastewater treatment systems.

Author: Nguyen Ly and Miyuki Thirumurthy | Biosensing Instrument | Published June 18th, 2025

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Note References
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