A subscription to JoVE is required to view this content. Sign in or start your free trial.
Presented here is a method for extracting microplastics from soil and identifying their polymer types. The method has been optimized for execution, applicability, and cost-effectiveness. It lays a scientific foundation for standardizing the analytical method to identify microplastics in soils.
Microplastics (MPs) pollution in the terrestrial environment has received increasing attention over the last decade, with increasing studies describing the numbers and types of MPs in different soil systems and their impacts on soil and crop health. However, different MPs extraction and analytical methods are used, limiting opportunities to compare results and generate reliable evidence for industry advice and policymakers. Here, we present a protocol that describes the methodology for sampling, separation, and chemical identification of conventional MPsΒ from soil. The method is low-cost, and the materials are readily available. This enhances operational ease and may help with widespread adoption. The protocol provides detailed information on sample collection from the top 0-30 cm of soil using plastic-free utensils; simulation of different soil types through the use of various solid media (such as bentonite clay, silicon dioxide, and non-contaminated soil), with the addition of the same massΒ of polyethylene(PE)-MPs for subsequent quantification; density separation of plastic particles utilizing saturated sodium chloride (NaCl) solution and digestion of organic impurities in the supernatant using 4 M sodium hydroxide (NaOH) solution; quantification of particles using fluorescent microscopy after Nile Red staining; and polymer identification using microΒ Fourier-Transform Infrared Spectroscopy (ΞΌ-FTIR) or Laser-Direct Infrared (LDIR) spectroscopy. The MPs recovery rate ranged from 83% - 90% for the abovementioned media. This protocol presents an efficient method for soil MPs analysis that is optimized for feasibility, applicability, and cost-effectiveness. Moreover, the video accompanied can guide the process of analyzing the soil MPs step-by-step virtually. This study is dedicated to standardizing the methods for soil MPs analysis, enhancing the connectivity and comparability of measurements, and establishing a foundation for more standardized and scientific research.
It is estimated that 4.8 to 12.7 million metric tons of plastic enter the ocean annually from terrestrial sources1,2. These plastic particles gradually degrade into smaller fragments in response to ultraviolet irradiation, mechanical abrasion, and biodegradation3,4. Microplastics (MPs) pollution, with plastic particles of diameter less than 5 mm, in the soil is becoming an increasing concern, particularly in terms of its potential effect on soil and crop health. It is primarily driven by the continual rise in plastic production and challenges surroundi....
NOTE: The following solutions need to be prepared at ambient temperature prior to the extraction process: 1) Saturated NaCl solution (5.7 M) - dissolve 1 kg of NaCl in 3 L DI H2O; 2) 4 M NaOH - dissolve 480 g NaOH in 3 L DI H2O; 3) Nile Red (100 Β΅g mL-1) - dissolve 10 mg of Nile Red in 100 mL of appropriate solvent (e.g., methanol, acetone).
1. Soil sampling and preparation
To validate the recovery rates of this methodology, samples from three different solid matrices (silicon dioxide (SD), bentonite clay (BT), and soil) were analyzed in sets of three replicates. Samples were analyzed with and without the addition of 0.04% w/w white polyethylene (PE) microplastic (particle size range 40-48 Β΅m). Soil samples were collected from Haidian District, Beijing, China (China Agricultural University West Campus), and soil was classified as umber soil. Additionally, three replicates of b.......
The soil sampling strategy in the field, including approaches such as simple random sampling or systematic grid sampling, as well as the sampling area and depth, must be tailored to the specific research questions and clearly defined prior to the sample collection. Some studies have focused on the topsoil layer of 0-10 cm34,37, whereas other collected soil samples with a depth of 0-40 cm38. Since the size and abundance of MPs vary in diffe.......
The authors have nothing to disclose.
This project was supported by the Science and Technology Major Project of Ordos, China [ZD20232320]; the UKRI Global Challenges Research Fund (GCRF) and the Natural Environment Research Council project, "Do agricultural microplastics undermine food security and sustainable development in less economically developed countries?" under Grant [NE/V005871/1]; and the National Natural Science Foundation of China under Grant [42277097]; the High-level Team Project of China Agricultural University, Professor station of China Agricultural University at Xinzhou Center for Disease Control, and Prevention and Basic Research Program in Xinzhou, Shanxi Province [20230515] a....
Name | Company | Catalog Number | Comments |
2-decimal balance | n/a | n/a | Standard 2-decimal balance |
40 Β°C oven | n/a | n/a | Standard large fan-oven with temperature set to 40 Β°C |
8700 LDIR | Agilent Technologies | n/a | LDIR used to identify particles |
Aluminum container | n/a | n/a | Standard aluminum food take-away container |
Aluminum foil | n/a | n/a | Standard heavy-duty aluminum foil |
Axioplan 2 | Zeiss | n/a | Fluorescence microscopy is used to observe microplastic particles in the fluorescent state |
Bentonite clay | Sigma Aldrich | 285234 | Bentonite clay used for recovery tests |
BX53 | Olympus | n/a | Fluorescence microscopy is used to observe microplastic particles in the fluorescent state |
Glass beaker (600 ml) | n/a | n/a | Standard glass beaker |
Glass bottle (1 l) | n/a | n/a | Standard glass bottle |
Glass magnetic stirrer bar | n/a | n/a | Standard glass coated magnetic stirrer bar |
Glass measuring cylinder (500 ml) | n/a | n/a | Standard glass measuring cylinder |
Glass pipette (10 ml) | |||
Glass vacuum filtration device | Pyrex (purchased via Sigma Aldrich) | SLW5809/KIT | Glass filtration device with 500 ml funnel, porous plate, and 1 l collection beaker |
LUMOS Alpha II | Bruker | n/a | FTIR used to analyze suspect microplastics. |
Magnetic stirring plate | n/a | n/a | Standard magnetic stirring plate |
MCE filter membrane | Jinteng company | JTMF0441/0442 | White MCE membranes, 0.2 Β΅m pore size, 50 mm diameter, with FTIR method |
Nile Red | Fisher Scientific | 10464311 | Nile Red powder used to make stock solution of nile red dye using appropriate solvent (e.g. acetone) |
PCTE filter membrane | Sterlitech Corporation | 1270060 | Black PCTE membranes, PVP-free, 0.2 Β΅m pore size, 47 mm diameter, with LDIR method |
Silicon dioxide | Sigma Aldrich | 18649 | Silicon dioxide used for recovery tests |
Sodium chloride | Sigma Aldrich | S9888 | Sodium chloride used for density separation |
Sodium hydroxide | Fisher Scientific | 10675692 | Sodium hydroxide used for organic matter digestion |
Soil auger | n/a | n/a | Length 30 cm; diameter 2 cm; material stainless steel |
Ultra-high molecular weight polyethylene microplastic powder | Sigma Aldrich | 434272 | Polyethylene microplastic used to spike silicon dioxide, bentonite clay, and soil samples for recovery tests |
Vacuum pump | Vacuubrand GmBH Co KG | ME 2C NT | Vacuum pump for vacuum filtration |
Request permission to reuse the text or figures of this JoVE article
Request PermissionThis article has been published
Video Coming Soon
Copyright Β© 2025 MyJoVE Corporation. All rights reserved