Microplastic Sensing: A Major Global Problem

In the global effort to regulate microplastics and nanoplastics (MNPs), large-scale detection of these pollutants remains a significant challenge. The lack of standardized methods and detailed characterization of MNP concentrations in different environments compromises both the effectiveness of legislation and public awareness of this issue [Yang, Y. (2021)].

The vast diversity in size, composition, and shape of MNP particles, combined with the variability of the environments where they are found, makes their detection and quantification a complex task. Existing methods often struggle to accommodate these variations and may fail to provide consistent and accurate results [Jin, M. et al. (2022)].

Recently, advances have been made in the search for more effective alternatives to detect and quantify MNPs. Established technologies such as Fourier-transform infrared spectroscopy (FTIR), scanning electron microscopy (SEM), and fluorescence-based techniques have been refined to handle the diversity and complexity of these particles [Li, J., Liu (2017)]. On the other hand, emergent electrochemical methods represent a potential alternative for rapid, low cost, user-friendly, sensitive and reproducible quantification of microplastics [Dong, H. et al.].

In particular, electrochemical biosensors are a powerful system to boost specificity since their responses are mediated by target recognition through an electrode-tethered bioreceptor. Beyond their primary role in quantifying the analyte with enhanced analytical performance, such biosensing devices can also be used to study the bioreceptor/target binding kinetics and thermodynamics. For instance, they can be used to determine the affinity constant involved in these interactions, along with the number of binding sites [Fu, K. et al.]. These insights are essential for experimentally reaching a more comprehensive understanding of the protein proposed by our project (our project).

Therefore, the fabrication and validation of hardware suitable for coupling with genetically engineered proteins aimed at contaminant quantification could serve dual purposes. It offers a fast and cost-effective solution for experimentally determining the dissociation constant, which is crucial for advances in synthetic biology. At the same time, it provides a highly accurate method for contaminant sensing, a significant global challenge.

The Journey of Microplastic Detection Techniques throughout the B.A.R.B.I.E. Project

In this section, we present an overview of recent high-impact works on the detection of micro- and nano plastics.

In general, electrochemical alternatives for the detection of MNPs aim to quantify both the concentration and the average size of particles. However, a significant challenge is dealing with sensitivity and specificity when interrogating the devices with real and complex samples, which can introduce various types of interferences, e.g., nonspecific adsorptions. These interferences can arise from macromolecules and particles similar in size and electrochemical properties of MNPs or from the interaction of MNPs with different molecules on their surfaces [Lv, L. et al, 2019].

Currently, the main established methods for detecting micro and nanoplastics include image-based methods such as optical microscopy [TM. Garcia. et al, 2020][Zhou, G. et al, 2020], fluorescence microscopy [Kankanige, D. et al, 2021], electron microscopy [Vilakati, B. et al, 2020][Emre Çomaklı et al, 2020], and spectroscopy-based methods such as Fourier-transform infrared (FTIR) [Fred-Ahmadu et al, 2020][Mattsson, K. et al, 2021][Rowley, K. H. et al, 2020] and Raman spectroscopy [Allen, S. et al, 2019][Zhao, S. et al, 2015]. The primary limitation of these techniques is the time required for analysis and the restrictions in point-of-care determination of microplastics. Moreover, none of these characterizations are sufficiently precise on their own, necessitating a combination of techniques to obtain reliable results. For instance, image-based techniques might be used to identify particles and their sizes, while spectroscopy is employed to determine the composition and degradation state of the MNP. There are also approaches that allow coupling microscopy analysis with spectroscopy, such as μ-FT-IR or μ-Raman [Rathore, C. et al, 2023][Amato-Lourenço, L. F. et al, 2024], though these systems are typically sensitive only to particles larger than ~10 μm [Unnimaya, S. et al, 2023].

Recent approaches explore the use of electrochemical arrays for the detection and quantification of MNPs. In 2021, Colson and Michel proposed using impedance spectroscopy to detect individual plastic particles within a microfluidic channel coupled with an electrochemical working cell [Michel, A. P. M. et al, 2021]. In this setup, the passage of microplastics was individually detected by a peak in the impedance scan. Moreover, using the real and imaginary parts of the impedance measured at six different current frequencies, a machine learning model was trained to distinguish signals from polymeric particles, biological residues, or other sediments of similar size, enhancing the sensor's prediction capability. This method advanced the detection of microplastics due to its precision, speed, and scalability. However, the results showed a considerable drop (≈ 50%) in sensitivity for microplastics smaller than 200 μm.

In 2022, Ching et al proposed an impedance-based sensor to predict the concentration, composition, and size of microplastics in water [Ching et al, 2022]. This system relied on static sample measurements and used the k-nearest neighbors algorithm for predictions. Although sensitive for microplastics larger than 20 μm, the proposed sensor had a limitation in selectivity, affecting its use in real samples. In 2023, H Du et al proposed a graphene-based impedance sensor capable of enhancing selectivity for micro and nanoplastics [Du, H. et al, 2023]. Although similar to other electrochemical sensors, this system employed machine learning techniques, such as principal component analysis, to integrate signals from impedance measurements across multiple frequencies. Despite its innovative approach, the method faced reproducibility challenges in microplastic detection. Furthermore, the sensor lacked a selective recognition element for MNPs beyond the machine learning analyses, limiting its specificity in detecting these pollutants.

More recently, in April 2024, Z Xiao et al proposed a photoelectrochemical biosensor based on the aggregation effect of MNPs driven by protein corona formation [Xiao, Z. et al, 2024]. In this sensor, an electrode with Cu3SnS4 nanostructures was fabricated, to which bovine serum albumin (BSA) was anchored. The aggregation effect induced by the interaction of BSA with MNPs was used to determine the concentration of MNPs through changes in the measured photocurrent. However, the specificity of this system is expected to be low because of the nonspecific character of this intermolecular interaction.

In conclusion, while electrochemical methods show promise for detecting MNPs by quantifying particle concentration and size, they encounter significant challenges when applied to complex real-world samples. Interferences from macromolecules or similarly-sized particles can compromise accuracy, and current approaches often require a combination of techniques to achieve reliable results. Recent advancements, including the integration of machine learning and the development of innovative sensor designs like impedance spectroscopy and photoelectrochemical biosensors, have enhanced sensitivity, scalability, and prediction capability. However, several challenges persist in detecting smaller MNPs and ensuring selectivity and reproducibility, underscoring the need for further innovation in this field.

Our Proposal

To address the urgent need for rapid, accessible, and accurate detection of MNPs in the B.A.R.B.I.E. project, we developed an electrochemical biosensor capable of quantifying micro- and nanoplastics (MNPs) by utilizing plastic-binding proteins as a recognition element coupled with a label-free electrochemical biosensor.

The sensing device consists of a gold microfabricated device on a glass substrate. Additionally, the device includes three electrodes: working, counter, and reference electrodes. This set of electrodes allows for faradaic charge-transfer reaction-mediated electrochemical measurements. Moreover, the active area of each electrode is photolithographically defined by the SU-8 polymer, which has been reported as essential for ensuring the reproducibility of measurements [Shimizu, F. M. et al, 2023].

The sensor is fabricated by cleaning a glass substrate, applying an HMDS adhesion layer, and patterning the design via photolithography. A Cr/Au metal layer is deposited, followed by liftoff and surface cleaning. The process concludes with SU-8 deposition and final cleaning. As a final result of the manufacturing process, 12 plates were obtained, each containing 8 different sensors. The figure below shows the resulting plate (Fig. 1).

Microfabricated gold sensor
Figure 1. Microfabricated gold sensor.

To construct the biosensor, the idea is using the plastic binding proteins (PBPs), which includes Barbie1, engineered by our team, that specifically binds to MNPs. The concentration of these particles is then quantified using square wave voltammetry (SWV) and an arrangement of a label-free biosensor with a redox probe in solution. To facilitate the quantification at the point-of-need, a handheld and low-cost one-channel potentiostat capable of performing EIS, SWV, and other electrochemical measurements was employed.

Furthermore, three distinct methods were employed to evaluate the sensor's performance:

  • Blank (BA): Utilizes the electrochemical chip without surface modification by the PBPs.
  • Bind (BI): Utilizes the electrochemical chip modified with the PBPs on the working electrode surface for faradaic SWV measurements.
  • Bulk (BU): Involves a prior process of bulky corona-protein formation with PBPs, analyzing the entire MNP-PBP complex adsorbed onto the working electrode.
Detection Methods Evaluation

We present different methods for identifying and quantifying micro and nanoplastics proposed in the project, discussing their advantages and disadvantages.

Blank (BA)

For the detection, MNPs are placed in an aqueous solution containing an electrolyte with a known electrochemical response. SWV technique can explore quickly and efficiently the work electrode surface occupation. Since the MNPs are small particles composed of a dielectric material, MNPs can trigger various electrochemical processes in the solution, such as hindering ion diffusion, accumulating charges on their surfaces, or filling the surface region of the blank working electrode. These effects impact the impedance and SWV measurements. While all these mechanisms can contribute to quantifying MNPs in water, other small materials present in the water can also affect the results to some extent.

Blank (BA) Biosensor representation
Blank (BA) Biosensor representation.

Deposited - Na2SO4

As an initial approach to exploring electrochemical sensing of MNPs, a solution of Na2SO4 was tested, which was reported to be effective for detecting microplastics.

First, EIS measurements were conducted with the blank sensor using a solution containing 0.5 M of Na2SO4. The typical Na2SO4 curves in the Bode plot are shown in Figure 2.

Bode Plot for Na2SO4
Figure 2. Electrochemical Impedance Spectroscopy of Na2SO4 electrolyte.

At higher frequencies, the impedance phase is below 45°, and the magnitude remains constant relative to the frequency, characteristics of a more resistive behavior. In the mid-to-low frequency range, the phase exceeds 45°, and the magnitude starts varying linearly with frequency, indicating a more capacitive behavior of the solution.

Based on the analysis of the electrolyte’s behavior, the circuit shown in Figure 3 was chosen to fit the EIS data. In this circuit, Na2SO4 solution is modeled as a resistor Rs and the interface between the work electrode and the solution is represented by a parallel combination of a capacitor Csurf and a resistor Rsurf, mathematically capturing the capacitive and resistive electrochemical processes occurring in the surface. It is expected that the presence of microplastics at the interface between the working electrode and the electrochemical solution will result in changes in the measured values of Rsurf and Csurf.

Equivalent Circuit for Na2SO4
Figure 3. Equivalent circuit for Na2SO4 electrolyte.

To verify the relationship between the concentration of MNPs and the electrochemical EIS response, each sensor was rinsed with 1 mL of deionized water, and PSNBs (1000 nm) were progressively added at concentrations of 0.01, 0.1, and 1 mg/L. At each stage, the samples were incubated for 10 minutes, measured in Na2SO4, and then rinsed with 2 mL of deionized water. The obtained values for Rsurf and Csurf were normalized against the blank (Na2SO4) and evaluated in relation to the PS (polystyrene) concentration, as shown in Figure 4.

EIS Fitting Results for Na2SO4
Figure 4. Equivalent circuit fitting results with Na2SO4 electrolyte.

The results of the equivalent circuit fitting using impedance spectroscopy in Na2SO4 solution yielded unsatisfactory R² values of 0.22 and 0.25, indicating a poor correlation between the modeled and experimental data. Additionally, the reproducibility was compromised causing excessively high deviations in the measurements. Essentially, we conclude that this approach was too simple to detect microplastics effectively.

Deposited - K3[Fe(CN)6]/K4[Fe(CN)6]

The K3[Fe(CN)6]/K4[Fe(CN)6 probe is widely used in electrochemical detection experiments due to its well-established oxidation and reduction processes in the literature. Additionally, the concentration of microplastics was evaluated using square wave voltammetry (SWV), a simple, fast method that demonstrated high reproducibility. This makes the results and conclusions obtained reproducible and valuable for future iGEM teams or other projects aiming to detect microplastics.

Due to the redox processes occurring with the K3[Fe(CN)6]/K4[Fe(CN)6 probe, SWV measurements show a current peak at a specific applied potential, where the maximum current (IMax) is related to the electroactive area of the working electrode. The PS concentration is thus connected to the surface coverage of the working electrode, and consequently to the measured IMax. To explore this relationship, samples of PSNBs (polystyrene nanobeads) (1000 nm) were progressively analyzed at concentrations of 0.01, 0.1, 1, 10, and 100 mg/L. At each stage, the samples were incubated for 10 minutes and washed with 2 mL of deionized water. The results for the analytical curve are shown in Figure 5.

Analytical Curve from SWV
Figure 5. Analytical curve from SWV K3[Fe(CN)6]/K4[Fe(CN)6] result.

While this approach yielded slightly better outcomes compared to the impedance spectroscopy method, the results remained inadequate, with R² values (~ 0.76) still falling short of acceptable levels (> 0.9). By depositing the MNPs in the surface and using SWV, there is a poor linearity and sensitivity. Thus, they are not expected to enable the determination of MNPs in real-world samples.

Bind (BI)

In the Bind (BI) methodology, the sensor is pre-modified by binding the target protein on the work electrode. After this process, the sample of micro- and nanoplastics (MNPs) dispersed in the electrolyte is brought into contact with the electrodes. The specific interaction between the plastic particles and the protein can produce electrochemical results that determine the concentration of the MNPs with minimal interference from other potential materials in the medium.

Bind (BI) Biosensor representation
Bind (BI) Biosensor representation.

Drop Casting - BaCBM2

To explore the effectiveness of using plastic-binding proteins for MNP sensing, the drop casting method was employed.

This protein immobilization method involves simple protein adsorption by depositing onto the substrate. SWV measurements were taken with the K3[Fe(CN)6]/K4[Fe(CN)6] probe for each clean sensor. After washing each device with 1 mL of PBS (10 mM), 5 µL of BaCBM2 protein (500 µg/mL) was added to the working electrode, followed by a 20-minute incubation.

After incubation, the devices were washed with 2 mL of PBS, and SWV measurements were taken again to define the blank. A decrease in current after protein deposition indicates the proteins were likely fixed to the surface. Each sensor was then washed again with 1 mL of PBS, and PSNBs (1000 nm) were progressively added at concentrations of 0.01, 0.1, 1, 10, and 100 mg/mL. The current from each SWV measurement was normalized relative to the blank to create an analytical curve based on the microplastic concentration.

BaCBM2 Drop Casting Analytical Curve
Figure 6: BaCBM2 Drop Casting Analytical Curve.

By using the BaCBM2 protein’s interaction with the MNPs, the results became significantly better, with R² going from 0.76 to 0.94 just by adding the protein. This already allows biosensing of microplastics. However, there is room for improvement, especially because the standard deviation between measurements is quite large, making the concentration values uncertain.

Self-Assembled Monolayers (SAMs) - BaCBM2

To ensure BaCBM2 immobilization and amplify the measured signal, the modification of the working electrode with three different self-assembled monolayers (SAMs) was tested: L-cysteine, cysteamine, and graphene oxide.

Methods of Protein Immobilization on the Gold Surface
Figure 7: Representation of different methods of protein immobilization on the gold surface. A) the simple adsorption of proteins (drop casting). B) SAM of cysteamine with interagent protein binding by C-terminal. C) SAM of L-cystein with interagent protein binding by N-terminal. D) SAM of graphene oxide with interagent protein binding by N-terminal.

First, SWV measurements were taken using the K3[Fe(CN)6]/K4[Fe(CN)6] (5 mM) probe on the clean sensors. Afterward, the sensors were rinsed with 1 mL of PBS to allow for SAM deposition. Each modification (L-cysteine, cysteamine, and graphene oxide) was performed on 4 different sensors. For this, 5 µL of each solution was added to the sensors at concentrations of 50 mM, 50 mM, and 2 mg/mL, respectively, for L-cysteine, cysteamine, and graphene oxide. The samples were then incubated at 4°C for 15 hours. After incubation, the sensors were washed with 2 mL of PBS per device, and SWV analysis was conducted with K3[Fe(CN)6]/K4[Fe(CN)6] (5 mM).

Following this, the devices were rinsed with 1 mL of PBS, and 5 µL of BaCBM2 protein solution (150 µg/mL) was added. The sensors were incubated with EDC:NHS (16.6:33.33 mM) for 45 minutes at 37°C. After incubation, each device was washed with 2 mL of PBS, and SWV measurements were taken again.

Next, the samples were rinsed with 1 mL of PBS before adding 5 µL of SuperBlock solution, which was incubated for 90 minutes. After this stage, each device was washed with 2 mL of PBS, and new SWV measurements were taken as a blank.

Finally, each sensor was washed again with 1 mL of PBS, and PSNBs (1000 nm) were progressively added at concentrations of 5, 10, 50, and 100 mg/L. At each step, the samples were incubated for 20 minutes and washed with 2 mL of PBS. The current obtained from each SWV measurement was normalized against the blank to create an analytical curve for the microplastic concentration, shown in Figure 8.

L-Cysteine SAM choice Cysteamine SAM choice Graphene Oxide SAM choice
Figure 8: Comparison of different SAM choices. A) L-Cysteine. B) Cysteamine. C) Graphene Oxide.

Based on initial tests, we concluded that the best method (R² > 0.85) was using cysteamine to bind the protein to the gold surface. By repeating the experiment with optimized parameters, we obtained an analytical curve with R² of 0.99, showing high precision in detecting even low concentrations of microplastic.

Cysteamine + BaCBM2 SAM Analytical Curve
Figure 9: Cysteamine + BaCBM2 SAM Analytical Curve.

Bulk (BU)

In the Bulk (BU) methodology, MNPs are initially placed in a solution containing a high concentration of target proteins. After a certain period, the surface of the particles is coated with these proteins, forming protein coronas (Model), thus, the interaction process occurs in the solution bulk. After this process, part of this solution is deposited specifically onto the working electrode. Following the immobilization of these MNP-protein complexes, an electrolyte is added to establish contact between the three electrodes.

Bulk (BU) Biosensor representation
Bulk (BU) Biosensor representation.

For the experimental tests of the bulk methodology, the BaCBM2 protein (150 µg/mL) and PSNBs (0.01, 0.1, and 1 mg/mL) were first mixed in PBS (10 mM) using a Microtube Rotating Mixer for 10 minutes to allow the formation of protein coronas. Following this, SWV measurements were performed using clean sensors. Next, a sample containing only 150 µg/mL of BaCBM2 in PBS, which was also shaken for 10 minutes, was incubated for 10 minutes to measure the blank by SWV, where a decrease of 26% in the peak current was observed. The four concentrations of PSNBs were then progressively incubated on the sensor. After each incubation, the sensor was washed with 2 mL of PBS (10 mM), followed by SWV measurement. The resulting analytical curve is presented in Figure 10.

Bulk BACBM2 + MNPs analytical curve.
Figure 10. Bulk BACBM2 + MNPs analytical curve.

Statistical Comparison of Detection Methods

Based on the results obtained for each detection method tested, it is possible to evaluate them in terms of several figures of merit. For our analysis, we evaluated, in addition to the R² metric, the mean standard deviation (σ) and the sensitivity (S), shown in equations 1, 2, and 3, where the space of the N_i analyzed concentrations is represented by i and the N_j replicates at each concentration are given by j.

Hardware Equation 1 < Hardware Equation 2 Hardware Equation 3

Therefore, based on the calculated values for the metrics, the linearity (R² normalized relative to the methods), the precision ((-1) * āσ normalized relative to the methods), and the sensitivity (S normalized relative to the methods) were analyzed in a more didactic manner. Thus, Figure 11 provides a comparative analysis of the detection methods.

Comparison between detection methods in terms of linearity, precision, and sensitivity.
Figure 11. Comparison between detection methods in terms of linearity, precision, and sensitivity.

In this analysis, we can observe how the first method evaluated (blank) is limited in terms of linearity (R² = 0.76) and precision (σ = 12.4 %), due to the absence of a recognition element. In contrast, the bind method using protein applied by drop casting showed a significant improvement in linearity (R² = 0.94), thanks to the presence of the BaCBM2 protein as a biological recognition element. However, it still exhibited poor precision (σ = 10.88 %), likely due to variability in the electrode modifications through this method.

bind method with BaCBM2 linked to a self-assembled monolayer (SAM) of cysteamine achieved high linearity (R² = 0.99) and excellent precision (σv = 0.88 %), owing to both the biological recognition element and a more precise fabrication method. Finally, the bulk method demonstrated good linearity (R² = 0.96) and precision (σ = 4.39 %), indicating the potential of this approach. However, more tests are needed to confirm its reliability. In terms of sensitivity, the methods presented similar results.

Dissociation Constant

on the results of the electrochemical assays, we demonstrated that it is possible to estimate the dissociation constant involved in the protein-plastic interaction.

1960, the analysis of the dissociation constant has been a studied method for evaluating the affinity between molecules through a binding assay [Colquhoun, D. (2006)][Yalow, R. S. et al (1960)]. In electrochemical assays based on Square Wave Voltammetry (SWV), the measured signal often depends on the occupancy of target molecules or particles (T) on the working electrode surface. This surface coverage (Θ) is influenced by the concentration of particles in the medium ([T]), the maximum surface coverage (Θ_{Max}), and the interaction between the target and the surface, which is related to the dissociation constant (K_d). The general expression for this process can be represented by the Langmuir isotherm [Hulme, E. C. et al (2010)], as shown in Equation 4.

Hardware Equation 4 <

Thus, the general graphs observed for this process can be analyzed in Figure 12. It illustrates a progressive surface filling with increasing target concentration. Additionally, when plotted against the logarithm of the target concentration, the graph shows an initial exponential region, followed by a linear region, and finally an asymptotic region at the end.

Typical Langmuir isotherm graphs.
Figure 12. Typical Langmuir isotherm graphs. (Left) Surface coverage as a function of T concentration. (Right) Surface coverage as a function of the logarithm of the concentration.

Langmuir isotherm approximation can be particularly useful in describing the measurements obtained from the self-assembled monolayers (SAM) in the bind (BI) methodology, as seen in the experiments conducted with the electrochemical sensor. During the incubation of PS particles on the working electrode, the interaction of particles with the affinity proteins (BaCBM2) follows the relationship described by Equation 4. As a result, surface coverage—and thus the measured signal—depends non-linearly on the concentration of PS in the medium, explaining part of the behavior observed in the obtained results.

In the second analytical curve, obtained with the cysteamine modification (Figure 8), a highly linear relationship (R² = 0.99) between the measured signal and the logarithm of PS concentration was observed. This suggests that, for this configuration, the chosen concentration range falls within the linear region of Figure 12. On one hand, this may indicate greater measurement precision30, but on the other hand, it precludes the estimation of maximum surface coverage and thus the dissociation constant.

Conversely, the first analytical curve generated with the cysteamine modification shows some saturation of the signal as log([PS]) increases (Figure 8.B), suggesting that the selected concentration range for this configuration is closer to the asymptotic region. While this may affect measurement precision, it allows for the estimation of the dissociation constant involved in the interaction between PSNBs and the surface in this system.

Thus, Equation 4 was applied to fit the data obtained from the first cysteamine modification, as shown in Figure 13.

Langmuir isotherm fit
Figure 13: Langmuir isotherm fit to SWV measurements of the sensor modified with cysteamine and BaCBM2.

Through this analysis, the dissociation constant (Kd) for PS particles binding to the surface of the working electrode was determined to be 15.13 mg/L. This value reflects the interaction between the anchored BaCBM2 proteins on the electrode and the plastic particles.

It is important to note that, although this value relates to the PS-protein interaction, it is influenced by various experimental factors such as temperature, stirring, incubation time, PS-gold interaction, protein-solution interaction, the reduced degrees of freedom of the protein after immobilization on the surface, among other factors. These variables complicate direct comparison with computationally predicted Kd values, for instance.

Nevertheless, despite the limitations when comparing computational data, this method of calculating the dissociation constant can be particularly useful for comparing the affinity of different proteins for PS particles, or more broadly, for any target molecule of interest.

Scanning Electron Microscopy

In order to characterize the MNPs interaction with the surface of the electrode, as well as the reusability of the sensor, Scanning Electron Microscopy (SEM) imaging was used. The SU-8 boundary, responsible for delimiting the active area of the working electrode, was characterized in Figure 14 and shown to have a thickness of 4.7 μm.

SU-8 active area boundary
Figure 14. SU-8 active area determining boundary seen from: A) Perpendicular view B) and C) 45° angled detector.
Working electrode images
Figure 15. A) Working electrode after Ar plasma cleaning. B) Working electrode with deposited PS MNPs.

Figure 15 demonstrates the effectiveness of using Ar plasma for cleaning the gold surface. This guarantees the quality of experiments that were carried subsequently on the same sensor.

MNPs on working electrode
Figure 16. MNPs deposited on the surface of the working electrode. A) PS particles accumulated near the SU-8 polymer boundary. B) Instance of particles chemically interacting. C) Physical imprints of particles left on the gold electrode surface.

X-ray Photoelectron Spectroscopy

To determine the composition of material deposited on the surface of the sensor, the technique of X-ray Photoelectron Spectroscopy (XPS) was utilized. This characterization allows us to determine whether the SAMs and the protein adhere properly to the gold surface after washing.

XPS spectrum of gold surface
Figure 17. XPS spectrum of the sensor surface. Left: Survey scans of the four samples. Right: Scan of the Gold 4f peaks with Gaussian curves fitted to determine peak height.

First, we look at the peaks of the 4f orbital of gold atoms for reference.

Nitrogen XPS spectrum analysis
Figure 18. XPS spectrum analysis. A) Nitrogen 1s orbital peaks. B) Nitrogen fit results after removing baseline and normalizing relative to the Au4f peaks.

Nitrogen is present on both the protein and the cysteamine, but it is more abundant on the protein because of the number of amino acids. Figure 18 is consistent with this expected result and shows both cysteamine and BaCBM2 remained fixed on the surface.

Sulfur XPS spectrum analysis
Figure 19. XPS spectrum analysis. A) Sulfur 2p orbital peaks. B) Sulfur fit results after removing baseline and normalizing relative to the Au4f peaks.

Finally, Figure 19 confirms this result by demonstrating the presence of the sulfur from the cysteamine monolayer on the surface. The drop casting also generates a sulfur peak due to the cysteine group of the protein itself, although less abundant than the SAM.

Experimental Information

We shared some experimental specifications regarding the manufacturing and cleaning processes of the sensors, electrochemical assays, and measurements used, with the aim of making the hardware more accessible for new projects.

The chosen architecture for the electrochemical sensor, as well as the fabrication methodology, were based on the device proposed by Flavio M. Shimizu and Anielli M. Pasqualeti et al. [Shimizu, F. M. et al, 2023].

1. Glass Substrate Preparation: The sensor fabrication begins with a glass substrate (25.4 × 76.2 mm) (Fig. 20). First, the glass substrate is cleaned using N2 plasma.

Glass substrates

Figure 20. Glass substrates

2. HMDS Adhesion Layer: After cleaning, a 2.3 μm thick layer of HMDS adhesion promoter is deposited on the substrate by spin coating (4000 RPM for 30 seconds) (Fig. 21). The plate is then heated at 100 °C for 3 minutes.

HMDS spin-coating

Figure 21. HMDS spin-coating

3. Photoresist Deposition: A layer of positive photoresist AZ4220 (Fig. 22) is applied by spin coating (4000 RPM for 30 seconds), followed by heating at 100 °C for 5 minutes.

Positive photoresist AZ4220 deposition

Figure 22. Positive photoresist AZ4220 deposition

4. Photolithography and Development: The sensor’s architecture is patterned using the mask aligner (MJB3, Karl Suss) with 15 seconds of exposure to light (Fig. 23). After exposure, the architecture is developed using AZ4000 developer for 3 minutes, followed by rinsing with water, nitrogen jet cleaning, and O2 plasma treatment (100W and 70 mT for 2 minutes).

Mask aligner (MJB3, Karl Suss) during light exposition process

Figure 23. Mask aligner (MJB3, Karl Suss) during light exposition process

5. Metal Layer Deposition: After developing the positive resist, a 20 nm layer of chromium (Cr) and a 100 nm layer of gold (Au) are deposited onto the substrate (Fig. 24).

Substrates prepared for metal deposition

Figure 24. Substrates prepared for metal deposition

6. Liftoff Process: The next step is the liftoff process, where the photoresist is dissolved in acetone, removing the Cr/Au layers that were on top of the resist.


7. Surface Cleaning and Hydrophilization: The surface is cleaned and hydrophilized using O2 plasma treatment (100W and 100 mT for 2 minutes).

8. SU-8 Deposition: A 5.4 μm thick layer of SU-8 is deposited by spin coating (1300 RPM for 25 seconds), followed by a pre-bake at 65 °C for 2 minutes and 95 °C for 5 minutes.

9. Photolithography for SU-8: The defined pattern for the SU-8 layer is photolithographed using the mask aligner (MJB3, Karl Suss) with 15 seconds of exposure (Fig. 25), followed by post-baking at 75 °C for 1 minute and 95 °C for 3 minutes.

Mask aligner (MJB3, Karl Suss) being operated

Figure 25. Mask aligner (MJB3, Karl Suss) being operated

10. Development of SU-8: The SU-8 pattern is developed using Metoxy-2-acetate developer (30 seconds for development, 30 seconds for rinsing).


11. Final Cleaning: The final step involves cleaning the surface with O2 plasma treatment (100W and 100 mT for 2 minutes) (Fig. 26).

Ar plasma cleaning of the chips

Figure 26. Ar plasma cleaning of the chips

Chemical Reagents

Milli-Q ultrapure water mΩ × cm; phosphate-buffered saline (PBS); sodium sulfate (Na2SO4); potassium nitrate (KNO3); potassium ferricyanide (K3[Fe(CN)6]); potassium ferrocyanide (K4[Fe(CN)6]); 1-Ethyl-3-(3-dimethylaminopropyl) carbodiimide (EDC); N-hydroxysuccinimide (NHS); SuperBlock™ Blocking Buffer (Thermo Scientific™); L-cysteine; cysteamine; graphene oxide (GO) and micro and nanoplastics standard samples polystyrene nanobeads (PSNBs).

Experimental Setup for Electrochemical Measurements

To perform the measurements, the fabricated device was connected to the PalmSens4 potentiostat through a connector developed at the Brazilian Nanotechnology National Laboratory (LNNano). The experimental setup is shown in Figure 27, where the three connections for the working, counter, and reference electrodes can be seen. Additionally, it is worth noting that the potentiostat used is portable, allowing for easy transport over long distances.

Connection between the device and potentiostat in the electrochemical measurements

Figure 27. Connection between the device and potentiostat in the electrochemical measurements

Electrochemical Impedance Spectroscopy (EIS) Measurement Parameters

  • Equilibration time: 5 s
  • Scan type: Default
  • Potential: 0.01 V
  • Signal: Sinusoidal
  • Number of frequencies: 25; 4.8/dec
  • Frequency range: 10,000 - 1 Hz

Square Wave Voltammetry (SWV) Measurement Parameters

  • Repetitions: 3
  • Equilibration time: 5 s
  • Initial potential: -0.1 V
  • Final potential: 0.4 V
  • Step: 0.0035 V
  • Amplitude: 0.035 V
  • Frequency: 15 Hz

Plasma Cleaning

Argon plasma cleaning was performed before each detection methodology to ensure the removal of potential contaminants, organic molecules, and to increase the hydrophilicity of the gold electrodes, facilitating electrochemical measurements. The parameters used were:

  • Power: 100 W
  • Pressure: 100 mT
  • Time: 5 minutes
Applications and Perspectives

We discussed possible applications of the proposed hardware and perspectives regarding the idea or potential new experimental validations.

Production Cost of the Hardware

The cost estimation for production was based on a previous assessment conducted by Drs. Gobbi, Shimizu, and Pasqualeti, where they evaluated the production cost of a batch containing 16 slides, with 8 devices on each slide, totaling 128 devices. Table 1 shows the costs considered for the estimation:

Cost Component Amount (USD)
Materials: glass substrate, HMDS, AZ4220 photoresist, gold, chromium, SU-8 polymer, and manufacturing supplies 338
Specialized labor 366
Use and wear of equipment 215
Total cost per batch (128 devices) 919
Total cost per device 7.2

Microplastics Sensoring and Regulation

As shown in the integrated human practices (HP) (link to integrated human practices (HP)), at the beginning of the project, some discussions and meetings were held with specialists in the field of microplastics in Brazil. Specifically, during the meeting with Dr. Walter Waldman, the issue of the difficulty in quantifying microplastics in situ, especially in underdeveloped regions, was raised, mainly due to the lack of specialized equipment for this analysis.

Based on this feedback from a potential user of our device, changes were made to make our device more user-friendly and portable, such as adapting it to a portable potentiostat, enabling the determination of microplastics in different conditions. For this, the results presented here for the quantification of microplastics are extremely promising for the following reasons:

  • Use of widely employed electrochemical detection techniques: These methods are applied in various fields, such as disease diagnostics [Castro, A. C. H. et al.], food product quality control [Gambarra-Neto, F. F. et al.], fuel quality monitoring [Shimizu, F. M. et al.], and industrial processes [Giordano, G. F. et al.].
  • Portability of the detection method: The entire experimental apparatus can be transported in a case and operated via a notebook, facilitating adaptation for in situ characterizations.
  • Established manufacturing methods with high scalability: These methods are well-established in industry and can be scaled up [Madou, Marc J.].
  • Increased selectivity due to the protein used: Typically, microplastic detection methods rely on the electrical response of each material, enhancing selectivity through machine-learning models. However, false positives may arise if an extensive range of contaminants is not considered in the training of these models. The use of a biological element, like a protein, offers a more specific chemical affinity for micro- and nanoplastics, providing higher selectivity.

Future Prospects

Moreover, the development of this electrochemical biosensor model opens up several future prospects:

  • Adaptable platform for other genetically engineered proteins: The proposed sensor architecture, along with the self-assembled monolayer modification with cysteamine, enables the integration of different types of proteins into the sensor through the EDC/NHS reaction. Combined with the B.A.R.B.I.E. project’s pipeline for optimizing protein affinity to various contaminants, this could lead to a multi-purpose platform for detecting contaminants in water.
  • Analysis of complex samples: The bulk methodology, for example, involves a prior stage of protein-particle complex formation and could be combined with affinity-based purification methods for pre-treating complex samples containing microplastics, followed by electrochemical quantification. While this possibility is still distant, it is opened up through the use of genetically engineered proteins.

A Platform for Protein Optimization

As previously discussed, the possibility of experimentally estimating the dissociation constant (Kd) for the interaction between a protein and the molecule of interest paves the way for using this type of electrochemical device as a fast, low-cost, and adaptable experimental validation tool for different types of proteins and target molecules.

One potential way to integrate the computational pipeline would be to perform the proposed optimization, computationally finding the sequence with the lowest dissociation constant for a given contaminant. The original and optimized proteins could then be expressed in the laboratory, with modifications applied to the platform for each protein. Langmuir curves would be generated using the chosen contaminant's concentrations, allowing for an experimental determination of whether the optimized protein indeed shows a lower dissociation constant.

Looking ahead, a perspective for enhancing large-scale analysis would be to validate this methodology for architectures that support high-throughput electrochemical assays. This approach would enable the simultaneous testing of a wide range of proteins and molecules, optimizing the discovery and validation process of molecular interactions in a more robust experimental framework [Ayres, L. B. et al (2024)].


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