Name: Forming Micro-and Nano-Plastics from Agricultural Plastic Films for Employment in Fundamental Research Studies (Video) | JoVE Journal
Uploaded: 2022-07-27T14:15:00.000+00:00
Duration: 8 min 21 s
Description: Learn to prepare engineered micro and nanoplastics from polymer feedstocks using cryogenic milling and wet grinding. This mechanical method creates authentic model materials for environmental pollution research.

ai_agent_IP

ai_agent

maintenance

instantTrialDurationMinutes

isBiopharma

enableNewMyJoveSectionDesign

educationFeatures

seoMetaApi

ai_copilot_institution_blacklist

ai_chat_institution_blacklist

freeAccessWindow

ssoRoleCapture

scheduledMaintenanceBanner

joveLabsFeatures

disable_autoplay_for_bots

extended_trial_duration

5 minutes

This research was funded by the Herbert College of Agriculture, the Biosystems Engineering and Soil Department, and the Science Alliance at the University of Tennessee, Knoxville. Furthermore, the authors gratefully acknowledge the financial support provided through the USDA Grant 2020-67019-31167 for this research. The initial feedstocks for preparing MNPs of PBAT-based biodegradable mulch film were kindly provided by BioBag Americas, Inc. (Dunevin, FL, USA), and&#160;PBAT pellets by Mobius, LLC (Lenoir City, TN).

The authors have nothing to disclose.

This method describes an effective process initially described in a previous publication29, to prepare MNPs sourced from pellets and mulch films for environmental studies. The size reduction process involved cryogenic cooling (for film only), dry milling, and wet grinding stages, to manufacture model MNPs. We have applied this method to prepare MNPs from a wide range of polymeric feedstocks, including low-density polyethylene (LDPE), polybutyrate adipate-co-terephthalate (PBAT), and polylactic aci...

In recent decades, the rapidly increasing global production of plastics and improper disposal and lack of recycling for plastic waste has led to environmental pollution that has impacted marine and terrestrial ecosystems1,2,3. Plastic materials are essential for contemporary agriculture, particularly to cultivate vegetables, small fruit, and other specialty crops. Their usage as mulch films, high and low tunnel coverings, drip tape, and other applications aim to enhance crop yield and quality, lower production costs, and promote sustainable farming methods4,5. However, the expanding employment of &#34;plasticulture&#34; has raised concerns about the formation, distribution, and retention of plastic pieces in agricultural environments. After a continuous fragmentation process caused by embrittlement through environmental degradation during service life, larger plastic fragments form micro- and nanoplastics (MNPs), which persist in soil or migrate to adjacent waterways via water runoff and wind6,7,8. Environmental factors such as ultraviolet (UV) radiation through sunlight, mechanical forces of water, and biological factors trigger plastic embrittlement of environmentally dispersed plastics, resulting in the breakdown of larger plastic fragments into macro- or meso-plastic particles9,10. Further defragmentation forms microplastics (MPs) and nanoplastics (NPs), reflecting particles of average size (nominal diameter; dp) of 1-5000 &#181;m and 1-1000 nm, respectively11. However, the upper dp limit for NPs (i.e., a lower limit for MPs) is not universally agreed upon and&#160;in several papers, this is listed as 100 nm12.
MNPs from plastic waste pose an emerging global threat to soil health and ecosystem services. Adsorption of heavy metals from freshwater by MPs led to an 800-fold higher concentration of heavy metals compared to the surrounding environment13. Furthermore, MPs in aquatic ecosystems pose multiple stressors and contaminants by altering light penetration, causing oxygen depletion, and causing adhesion to various biota, including penetration and accumulation in aquatic organisms14.
Recent studies suggest that MNPs can impact soil geochemistry and biota, including microbial communities and plants15,16,17. Furthermore, NPs threaten the food web17,18,19,20. Since MNPs readily undergo vertical and horizontal transport in soil, they can carry absorbed contaminants such as pesticides, plasticizers, and microorganisms through the soil into groundwater or aquatic ecosystems such as rivers and streams21,22,23,24. Conventional agricultural plastics such as mulch films are made from polyethylene, which must be removed from the field after usage and disposed of in landfills. However, incomplete removal leads to substantial plastic debris accumulation in soils9,25,26. Alternatively, soil-biodegradable plastic mulches (BDMs) are designed to be tilled into the soil after use, where they will degrade over time. However, BDMs persist temporarily in soil and gradually degrade and fragment into MPs and NPs9,27.
Many current environmental ecotoxicological and fate studies employ idealized and non-representative MPs and NPs model materials. The most commonly used surrogate MNPs are monodisperse polystyrene micro- or nanospheres, which do not reflect the actual MNPs residing in the environment12,28. Consequently, the selection of unrepresentative MPs and NPs may result in inaccurate measurements and results. Based on the lack of appropriate model &#924;NPs for terrestrial environmental studies, the authors were motivated to prepare such models from agricultural plastics. We previously reported on the formation of MNPs from BDMs and polyethylene pellets through mechanical milling and grinding of plastic pellets and film materials and the dimensional and molecular characteristics of MNPs29. The current paper provides a more detailed protocol for preparing MNPs that can be applied more broadly to all agricultural plastics, such as mulch films or their pelletized feedstocks (Figure 1). Here, to serve as an example, we chose a mulch film and spherical pellets of the biodegradable polymer polybutylene adipate terephthalate (PBAT) to represent agricultural plastics.

<table><tbody><tr><td>Aluminum dish, 150 mL&amp;nbsp;</td><td>Fisher Scientific, Waltham, MA, USA</td><td>08-732-103</td><td>Drying of collected NPs</td></tr><tr><td>Aluminum dish, 500 mL</td><td>VWR International, Radnor, PA, USA</td><td>25433-018</td><td>Collecting NPs after wet-grinding</td></tr><tr><td>Centrifuge</td><td>Fisher Scientific, Waltham, MA, USA</td><td>Centrific 228</td><td>Container for centrifugation</td></tr><tr><td>Delivery tube, #20, 840 &amp;micro;m</td><td>Thomas Scientific, Swedesboro, NJ, USA</td><td>3383M30</td><td>Sieving of the first fraction during milling</td></tr><tr><td>Delivery tube, #60, 250 &amp;micro;m</td><td>Thomas Scientific, Swedesboro, NJ, USA</td><td>3383M45</td><td>Sieving of the second fraction (3x)&amp;nbsp; during milling</td></tr><tr><td>Thermomixer,&amp;nbsp; 5350 Mixer</td><td>Eppendorf North America, Enfield, CT, USA</td><td>05-400-200</td><td>Analysis of sieving experiments</td></tr><tr><td>FT-IR Spectrum Two, spectrometer with attenuated total reflectance (ATR)</td><td>Perkin Elmer, Waltham, MA, USA</td><td>L1050228&amp;nbsp;</td><td>Measuring FTIR spectra</td></tr><tr><td>Glass beaker, 1000 mL</td><td>DWK Life Sciences, Milville, NJ, USA</td><td>02-555-113</td><td>Stirring of MPs-water slurry before grinding</td></tr><tr><td>Glass front plate</td><td>Thomas Scientific, Swedesboro, NJ, USA</td><td>3383N55&amp;nbsp;</td><td>Front cover plaste for Wiley Mini Mill</td></tr><tr><td>Glass jar, 50 mL</td><td>Uline, Pleasant Prairie, WI, USA</td><td>S-15846P</td><td>Collective MPs after milling</td></tr><tr><td>Glove Box, neoprene</td><td>Bel-Art-SP Scienceware, Wayne, NJ, USA</td><td>BEL-H500290000</td><td>22-Inch, Size 10</td></tr><tr><td>Zetasizer Nano ZS 90 size analyzer</td><td>Malvern Panalytical, Worcestershire, UK&amp;nbsp;</td><td>Zetasizer Nano ZS</td><td>Measuring nanoplastics dispersed in DI-water</td></tr><tr><td>Microscope camera</td><td>Nikon, Tokyo,&amp;nbsp;108-6290, Japan</td><td>Nikon Digital Sight 10</td><td>Combined with Olympus microscope to receive digital images</td></tr><tr><td>Microscope</td><td>Olympus, Shinjuku, Tokyo, Japan</td><td>Model SZ 61</td><td>Imaging of MPs</td></tr><tr><td>Nitrogen jar, low form dewar flasks</td><td>Cole-Palmer, Vernon Hills, IL, USA</td><td>UX-03771-23</td><td>Storage of liquid nitrogen during cryogenic cooling</td></tr><tr><td>Accurate Blend 200, 12-speed blender</td><td>Oster, Boca Raton, FL, USA</td><td>6684</td><td>Initiating the size reduction of cryogenically treated plastic film</td></tr><tr><td>PBAT film, - BioAgri&amp;trade; (Mater-Bi&amp;reg;)</td><td>BioBag Americas, Inc, Dunedin, FL, USA</td><td>0.7 mm thick</td><td>Feedstock to form MPs and NPs, agricultural mulch film</td></tr><tr><td>PBAT pellets</td><td>Mobius, LLC, Lenoir City, TN, USA</td><td>Diameter 3 mm</td><td>Feedstock to form microplastics (MPs) and nanoplastics (NPs) trough milling and grinding</td></tr><tr><td>Plastic centrifuge tubes, 50 mL</td><td>Fisher Scientific, Waltham, MA, USA</td><td>06-443-18</td><td>Centrifugation of slurry after wet-grinding</td></tr><tr><td>Plastic jar, 1000 mL, pre-cleaned, straight sided</td><td>Fisher Scientific, Waltham, MA, USA</td><td>05-719-733</td><td>Collection of NPs during and after wet grinding</td></tr><tr><td>Polygon stir bars, diameter&amp;oslash;=8 mm, length=50.8 mm&amp;nbsp;&amp;nbsp;</td><td>Fisher Scientific, Waltham, MA, USA</td><td>14-512-127</td><td>Stirring of MPs slurry prior to wet-grinding</td></tr><tr><td>Scissors, titanium bonded</td><td>Westcott, Shelton, CT, USA</td><td>13901</td><td>Cutting of initial PBAT film feedstocks</td></tr><tr><td>Square glass cell with square aperture and cap, 12 mm O.D.</td><td>Malvern Panalytical, Worcestershire, UK&amp;nbsp;</td><td>PCS1115</td><td>Measuring of NPs particle size</td></tr><tr><td>Stainless steel bottom, 3 inch, pan</td><td>Hogentogler &amp;amp; Co. Inc, Columbia, MD, USA</td><td>8401</td><td>For sieving after Wiley-milling</td></tr><tr><td>Stainless steel sieve, 3 inch, No. 140 (106 &amp;micro;m)</td><td>Hogentogler &amp;amp; Co. Inc, Columbia, MD, USA</td><td>1308</td><td>For sieving after Wiley-milling</td></tr><tr><td>Stainless steel sieve, 3 inch, No. 20 (850 &amp;micro;m)</td><td>Hogentogler &amp;amp; Co. Inc, Columbia, MD, USA</td><td>1296</td><td>Sieving of MPs after Wiley-milling</td></tr><tr><td>Stainless steel sieve, 3 inch, No. 325 (45 &amp;micro;m)</td><td>Hogentogler &amp;amp; Co. Inc, Columbia, MD, USA</td><td>1313</td><td>Sieving of MPs after Wiley-milling</td></tr><tr><td>Stainless steel sieve, 3 inch, No. 60 (250 &amp;micro;m)</td><td>Hogentogler &amp;amp; Co. Inc, Columbia, MD, USA</td><td>1303</td><td>Sieving of MPs after Wiley-milling</td></tr><tr><td>Stainless steel top cover, 3 inch</td><td>Hogentogler &amp;amp; Co. Inc, Columbia, MD, USA</td><td>8406</td><td>Sieving of MPs after Wiley-milling</td></tr><tr><td>Stainless steel tweezers</td><td>Global Industrial, Port Washington, NY, USA</td><td>T9FB2264892</td><td>Transferring of&amp;nbsp; frozen film particles from jar into blender</td></tr><tr><td>Vacuum oven, model 281A</td><td>Fisher Scientific, Waltham, MA, USA</td><td>13-262-50</td><td>Vacuum oven to dry NPs after wet-grinding</td></tr><tr><td>Friction grinding machine, Supermass Colloider</td><td>Masuko Sangyo, Tokyo, Japan</td><td>MKCA6-2J</td><td>Grinding machine to form NPs from MPs</td></tr><tr><td>Wet-grinding stone, grit size: 297 &amp;mu;m -420 &amp;mu;m</td><td>Masuko Sangyo, Tokyo, Japan</td><td>MKE6-46DD</td><td>Grinding stone to form NPs from MPs</td></tr><tr><td>Wiley Mini Mill, rotary cutting mill</td><td>Thomas Scientific, Swedesboro, NJ, USA</td><td>NC1346618</td><td>Size reduction of pellets and film into MPs and NPs</td></tr><tr><td>&lt;strong&gt;Software&lt;/strong&gt;</td><td></td><td></td><td></td></tr><tr><td>FTIR-Spectroscopy software</td><td>Perkin Elmer, Waltham, MA, USA</td><td>Spectrum 10&amp;nbsp;</td><td>Collection of spectra from the initial plastic, MPs and NPs</td></tr><tr><td>Image J, image processing program</td><td>National Institutes of Health, Bethesda, MD, USA</td><td>Version 1.53n</td><td>Analysis of digital images received from microscopy&amp;nbsp;</td></tr><tr><td>Microscope software, ds-fi1 software</td><td>Malvern Panalytical , Malvern, UK</td><td>Firmware DS-U1 Ver3.10</td><td>Recording of digital images</td></tr><tr><td>Microsoft, Windows, &amp;nbsp;Excel 365, spreadsheet software</td><td>Microsoft, Redmond, WA, USA</td><td>Office 365</td><td>Calculating the average particle size and creating FTIR spectra images</td></tr><tr><td>JMP software, statistical software</td><td>SAS Institute Inc., Cary, NC, 1989-2021</td><td>Version 15</td><td>Statistical analysis of particle size and perform best fit of data set</td></tr><tr><td>Unscrambler software</td><td>Camo Analytics, Oslo, Norway</td><td>Version 9.2</td><td>Normalizing and converting FTIR spectra into .csv fromat</td></tr></tbody></table>

forming micro-and nano-plastics from agricultural plastic films for employment in fundamental research studies

Forming Micro-and Nano-Plastics from Agricultural Plastic Films for Employment in Fundamental Research Studies

Microplastics (MPs) and nanoplastics (NPs) dispersed in agricultural ecosystems can pose a severe threat to biota in soil and nearby waterways. In addition, chemicals such as pesticides adsorbed by NPs can harm soil organisms and potentially enter the food chain. In this context, agriculturally utilized plastics such as plastic mulch films contribute significantly to plastic pollution in agricultural ecosystems. However, most fundamental studies of fate and ecotoxicity employ idealized and poorly representative MP materials, such as polystyrene microspheres.
Therefore, as described herein, we developed a lab-scale multi-step procedure to mechanically form representative MPs and NPs for such studies. The plastic material was prepared from commercially available plastic mulch films of polybutyrate adipate-co-terephthalate (PBAT) that were embrittled through either cryogenic treatment (CRYO) or environmental weathering (W), and from untreated PBAT pellets. The plastic materials were then treated by mechanical milling to form MPs with a size of 46-840 &#181;m, mimicking the abrasion of plastic fragments by wind and mechanical machinery. The MPs were then sieved into several size fractions to enable further analysis. Finally, the 106 &#181;m sieve fraction was subjected to wet grinding to generate NPs of 20-900 nm, a process that mimics the slow size reduction process for terrestrial MPs. The dimensions and the shape for MPs were determined through image analysis of stereomicrographs, and dynamic light scattering (DLS) was employed to assess particle size for NPs. MPs and NPs formed through this process possessed irregular shapes, which is in line with the geometric properties of MPs recovered from agricultural fields. Overall, this size reduction method proved efficient for forming MPs and NPs composed of biodegradable plastics such as polybutylene adipate-co-terephthalate (PBAT), representing mulch materials used for agricultural specialty crop production.

To validate the experimental procedure method and analysis, MPs and NPs were formed from pellets and film materials and compared by size and shape using microscopic images. The method described in Figure 1 efficiently formed MPs and NPs from biodegradable plastic pellets and films; this was achieved through cryogenic cooling, milling, and wet-grinding and characterization. The former step was unnecessary for environmentally weathered films because weathering induced embrittlement (Astner et ...

We show the formation and dimensional characterization of micro- and nanoplastics (MPs and NPs, respectively) using a stepwise process of mechanical milling, grinding, and imaging analysis.

Microplastics (MPs) and nanoplastics (NPs) dispersed in agricultural ecosystems can pose a severe threat to biota in soil and nearby waterways. In ...

forming-micro-nano-plastics-from-agricultural-plastic-films-for

Research

JoVE Journal

Engineering

Plastic films labeled "biodegradable" are commercially available for agricultural use as mulches.  Tillage represents an attractive disposal method, but degradation under field conditions is poorly understood.  The purpose of this study was to develop methods for isolating native soil fungi and bacteria that colonize plastic mulch films after field burial.

Isolation of Native Soil Microorganisms with Potential for Breaking Down Biodegradable Plastic Mulch Films Used in Agriculture

The protocol below describes the methodology for: microplastics sampling on the sea surface, separation of microplastic and chemical identification of particles. This protocol is in line with the recommendations for microplastics monitoring published by the MSFD Technical Subgroup on Marine Litter.

Protocol for Microplastics Sampling on the Sea Surface and Sample Analysis

Microplastics act as vector of potentially toxic organic contaminants with unpredictable effects. This protocol describes an alternative methodology for assessing the levels of organochlorine pesticides adsorbed on plastic pellets and identifying the polymer chemical structure. The focus is on pressurized fluid extraction and attenuated total reflectance Fourier transform infrared spectroscopy.

Extraction of Organochlorine Pesticides from Plastic Pellets and Plastic Type Analysis

Most microplastic research to date has occurred in marine systems where suspended solid levels are relatively low. Focus is now shifting to freshwater systems, which may feature high sediment loads and floating debris. This protocol addresses collecting and analyzing microplastic samples from aquatic environments that contain high suspended solid loads.

Sampling, Sorting, and Characterizing Microplastics in Aquatic Environments with High Suspended Sediment Loads and Large Floating Debris

This study detailed a reliable and cost-effective protocol for microplastics collection and detection from the daily use of plastic products.

Sampling, Identification and Characterization of Microplastics Release from Polypropylene Baby Feeding Bottle during Daily Use

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.

Separation and Identification of Conventional Microplastics from Farmland Soils

A method to quantify micro- and nano-plastics originating from polybutylene adipate terephthalate in soil using nuclear magnetic resonance spectroscopy is described here. This technique improves on existing methodology because it extends to quantification of nanoplastics and it can easily be adapted for processing environmental samples in bulk.

Quantification of Polybutylene Adipate Terephthalate-based Micro- and Nano-plastics from Soil Using Proton Nuclear Magnetic Resonance Spectroscopy

This protocol presents a scalable method for converting food waste into biodegradable polyhydroxyalkanoate (PHA) bioplastics. It utilizes arrested anaerobic digestion for food waste pretreatment, halophilic microbial fermentation for PHA biosynthesis, and a chemical-free downstream process for PHA recovery.

Scalable Step-by-Step Approach of Sustainable Bioplastic Production from Food Waste

Here, we provide a detailed description of sampling groundwater from a borehole for microplastics analysis using a patented sampling system developed for this purpose. The protocol details the methods for sampling microplastics from boreholes, as well as the separation and chemical identification of microplastics.

Sampling and Identification of Microplastics in Groundwater

A micropunching lithography approach is developed to generate micro- and submicron-patterns on top, sidewall and bottom surfaces of polymer substrates. It overcomes the obstacles of patterning conducting polymers and generating sidewall patterns. This method allows rapid fabrication of multiple features and is free of aggressive chemistry.

Micropunching Lithography for Generating Micro- and Submicron-patterns on Polymer Substrates

Learn to prepare engineered micro and nanoplastics from polymer feedstocks using cryogenic milling and wet grinding. This mechanical method creates authentic model materials for environmental pollution research.

Forming Micro-and Nano-Plastics from Agricultural Plastic Films for Employment in Fundamental Research Studies

Explore More Videos