The assessment of microplastics content in the environment is an indispensable part of environmental governance. Currently, common methods include laser infrared (LDIR), gas chromatography-mass spectrometry (GC-MS), and scanning electron microscope - energy dispersive x-ray spectroscopy (SEM-EDS). However, these methods either have the risk of misjudgment or have a long detection cycle, and the detection cost is generally expensive, which is not conducive to long-term evaluation of the effectiveness of governance for topics that require it.
Based on the problems of the current Polyethylene(PE) microplastics content detection methods, we designed a portable low-cost PE microplastics Content Detection Kit, which continuously supplies diluted soil test solution to the sample inspection center pool through a peristaltic pump. The working electrode in the sample inspection center pool is covered with functional supported lipid bilayers (SLBs), and the electrode, counter electrode, and reference electrode form a three-electrode system that outputs different electrochemical parameters depending on the different microplastics content of the test solution. By building a standard model in advance, we can decode these electrochemical parameters and obtain the microplastics content in the test solution.
Our PE microplastics content detection kit is dedicated to providing a portable and low-cost microplastics detection solution. In the design andassembly of this kit, we have fully, we have fully considered the possibility of different tasks for each component. The modular components can not only be used for microplastics detection, but also for other tasks.Microplastics content detection assembly can be divided into different new equipment, including a peristaltic pump, a sample center pool, and a portable electrochemical workstation.
In our PE microplastics content detection kit, we have designed a peristaltic pump that is responsible for delivering the test solution to the sample inspection center pool. Our peristaltic pump consists of four main components: an electric motor, a speed control circuit board, a rotating central axis, and a protective casing. Compared to traditional peristaltic pumps, we have introduced more flexibility in selecting peristaltic pump pulsation and rotation speed to cater to different operational requirements. In terms of pulsation selection, we have installed 12 detachable rolling shafts on the rotating central axis of the peristaltic pump to compress the delivery tube. Depending on research needs, the output pulsation of the peristaltic pump can be adjusted by detaching or attaching these rolling shafts. As for speed selection, we have incorporated a speed control circuit board between the power supply and the motor. Through the knob on the speed control circuit board, we can stepless adjust the pump's speed from 37 revolutions per minute (RPM) to 13 RPM.
The central shaft of the peristaltic pump will provide the power required for the pump's operation. The central shaft is fastened using screws and is easy to assemble and disassemble. The central shaft motor part is connected to the turntable part through motor fasteners, and users can choose different motors for replacement according to their own needs. The number of sub-axes can be changed in the rotary table part to achieve the selection of different pulses for the pump.
The peristaltic pump cover consists of two parts, top and bottom, and is the central location for the peristaltic pump to generate pulse output.
To achieve quantitative selection of peristaltic pump speed and adapt to different use environments, we selected a speed-regulating electrode plate.
The sample inspection center pool will provide a central place for the three-electrode system to detect microplastics content.
Record the electrical signals of the three-electrode system and output them.
1.2.4.1 Spatial distribution of the three electrodes
To meet the requirements of our system for gravitational potential, we chose to change the traditional vertical equidistant arrangement of the three-electrode system. We place the working electrode (glassy carbon electrode) horizontally, and place the counter electrode ( platinum wire electrode ) horizontally directly above the working electrode, reducing the distance between the working electrode and the counter electrode to reduce the impact of electrolyte resistance on potential control. On the contrary, the reference electrode (silver/silver chloride electrode) is placed vertically to avoid mutual interference with the reaction substances on the working electrode.
1.2.4.2 Counter electrode and reference electrode
The counter electrode, also known as the auxiliary electrode, is used to form a series circuit with the working electrode, and only plays a conductive role. In our system, we have chosen a platinum wire electrode.
The reference electrode is used as a reference to measure the potential difference relative to the research electrode. We selected a silver/silver chloride electrode as the reference electrode based on the pH value of the test solution.
1.2.4.3 Modified Working Electrode
We have chosen a glassy carbon electrode as our functional working electrode substrate. This electrode is a good inert electrode with good electrical conductivity, high hardness, high smoothness, high hydrogen overpotential, wide polarization range, and stable chemical properties, making it suitable for chemical modification electrodes.
To correlate the microplastics content with the electrical signals on the glassy carbon electrode, we chose to construct a SLBs on the surface of the glassy carbon sheet, and coupled the membrane with PE binding peptides and MscS transmembrane proteins.
This membrane can convert microplastics content into electrical
signal through the following pathway: when microplastics are
present in the environment, the PE binding peptide on the
functional SLBs specifically captures PE microplastics and
conducts membrane pressure signals to the MscS protein. Then the
MscS protein opens a positive ion channel and causes changes in
the electrical potential on the glassy carbon sheet.
MscS:
The Mechanosensitive Channel of Small Conductance (MscS) is an
ion channel in bacteria that rapidly responds to changes in
membrane tension. When a cell is swelling, MscS opens to
release ions, preventing the cell from bursting.
PEBP:
We initially use a Support Vector Machine (SVM) model to learn
from existing PE-binding peptides, creating a predictive
filter. We then expand the dataset, converting it into graph
structures for learning with a Graph Neural Network (GNN).
Additionally, we've developed a more accurate predictor that
incorporates an attention mechanism and the BLOSUM62 matrix.
By integrating the predictions from the SVM filter, GNN, and
the attention mechanism, and rigorously validating the model,
we've optimized its performance for practical application