How Microplastics Stunt Lentil Seeds Before They Even Sprout

  • Global plastic production reached 413.8 million metric tons in 2023, and a growing share of it is quietly fragmenting into the soil beneath our most vital food crops.
  • Research published in Chemosphere (De Silva et al., 2022) demonstrated that polyethylene microplastics at concentrations as low as 10 mg/L significantly hinder the internal biological activity of lentil seeds within just 6 hours of exposure โ€” before any visible germination signal appears.
  • How microplastics stunt lentil seeds operates through at least four converging pathways: physical blockage of soil pores, interference with seed water absorption, chemical leaching of toxic additives, and disruption of the soil microbial community.
How Microplastics Stunt Lentil Seeds Before They Even Sprout

Soil contamination with microplastics has become one of the most consequential, and least visible, agricultural problems of the 21st century. Global plastic production reached 413.8 million metric tons in 2023 (Frontiers in Plant Science, 2025), and estimates suggest that terrestrial ecosystems now hold up to four times more microplastic mass than the worldโ€™s oceans combined.

The Invisible Crisis Below Every Crop Field

Farmland sits at the center of this accumulation, receiving plastic particles through irrigation water, plastic mulch films, sewage sludge, and even fertilizer applications. A 2024 study published in Communications Earth and Environment found that microplastic concentrations in UK agricultural soils increased steadily between 1966 and 2022, with rates accelerating wherever organic or inorganic fertilizers were applied. The contamination is not a future risk. It is already embedded in the soil where crops grow right now.

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Seed germination is the most fragile and consequential stage in a plantโ€™s life. A seed that cannot germinate properly will never become a crop, no matter how fertile the soil above it appears. Most contamination research focuses on what happens after a plant has already emerged โ€” the effects of pollutants on leaf tissue, root elongation, or yield.

Far less attention has been paid to what happens before a seedling is visible at all, during the silent hours when a seed absorbs water, activates its enzymes, and attempts to push out its first root tip. This is the window where microplastics inflict some of their most damaging effects.

Lentils make the clearest case for studying this problem. They feed hundreds of millions of people across South Asia, the Middle East, and East Africa. They are a critical source of plant-based protein, iron, and folate, especially in regions where animal protein is too expensive. Their sensitivity to environmental stressors also makes them scientifically valuable as a model organism for detecting crop toxicity, which is why researchers chose lentils to test microplastic effects in some of the most precise experiments conducted to date.

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What Are Microplastics and Why Do They End Up on Farms

Microplastics are plastic particles smaller than 5 millimeters in their largest dimension. The term covers an enormous range of sizes and forms, from fragments a few millimeters across that you could see with the naked eye, down to nanoplastics smaller than 1 micrometer that require electron microscopy to detect.

The most relevant size range for seed germination research is the sub-5-micrometer fraction, which matches or falls below the diameter of soil pores and seed coat channels, making physical infiltration and blockage mechanically possible. Agricultural soils receive microplastics from several distinct pathways:

1. Plastic mulch films are the single largest source of microplastic input on farmland. Applied to suppress weeds and retain moisture, these thin polyethylene sheets fragment under ultraviolet radiation and physical tillage, leaving behind billions of polymer particles per hectare after just a few growing seasons. A 2024 study from Chinaโ€™s Guizhou province found microplastic concentrations in mulched soils ranging from 143 to 3,283 items per kilogram, with higher concentrations strongly correlated to longer mulching duration.

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2. Irrigation water carries microplastics from rivers, reservoirs, and groundwater systems that have already been contaminated by upstream industrial or municipal discharge. Every watering cycle deposits additional particles into the root zone.

3. Sewage sludge and biosolids used as organic fertilizers are a concentrated source of microplastics, since wastewater treatment plants capture particles from household and industrial sources but then apply the resulting sludge to agricultural fields. Research published in Communications Earth and Environment (2024) confirmed that fertilizer application, both organic and inorganic, significantly accelerated microplastic accumulation in long-term soil studies.

4. Plastic packaging waste from seeds, pesticides, and crop inputs breaks down in field margins and is incorporated into soil during tillage operations, adding to the ambient contamination load.

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5. Atmospheric deposition delivers microplastic fibers and fragments from distant urban and industrial sources through wind and rainfall, even onto fields far from obvious plastic waste sources.

Once deposited, microplastics resist biological degradation for decades. They do not dissolve, metabolize cleanly, or disappear between growing seasons. Each application of plastic on or near a field adds to a pool that accumulates in place.

How Plastic Particles Move Into and Through the Soil Ecosystem

Larger plastic items do not simply stay on the soil surface. Physical processes break them down and move them deeper into the soil profile in ways that compound the problem over time. Photodegradation (breakdown driven by ultraviolet light from the sun) initiates the fragmentation of plastic mulch films, causing surface embrittlement and cracking within one to two growing seasons. Mechanical tillage then grinds these brittle fragments into smaller and smaller particles that get mixed into the topsoil.

Freeze-thaw cycles in temperate climates accelerate the physical breakdown further, as water trapped inside cracks expands and widens those fractures with each winter. The net result is that one season of plastic mulch use generates a long tail of microplastic fragments that persist through subsequent crop cycles.

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Biological agents also contribute. Earthworms ingest soil particles including microplastics and excrete them deeper in the soil profile through their burrow systems. Research published in Environmental Science and Technology found that the biogenic incorporation rate of small microplastic fractions into earthworm burrow walls is high enough to create a genuine risk of particle transport into groundwater through preferential flow paths. Soil fauna, by trying to process and live within contaminated soil, end up redistributing the contamination vertically and laterally.

Water movement is equally important. Rain events and irrigation carry surface microplastics downward through soil macropores. In sloped agricultural fields, runoff also moves particles horizontally across the landscape, concentrating them in low-lying areas where many crops are grown because of superior moisture retention. This means that even fields with no direct plastic use history can accumulate microplastics transported from elsewhere.

Why Seed Germination Is the Most Vulnerable Stage

Germination is not a simple on-off event. It is a tightly sequenced biological process where each stage depends on the successful completion of the one before it, and where any disruption in the first few hours can silently determine whether a seedling ever emerges. The process begins with imbibition โ€” the absorption of water by the dry seed through tiny pores and channels in the seed coat. Water uptake activates dormant enzymes, triggers the breakdown of stored starches into usable sugars, and initiates cell elongation in the embryo.

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Without sufficient and uninterrupted water access during this phase, the seed cannot generate the metabolic energy needed to sustain growth. The imbibition phase in lentils begins within minutes of soil contact and reaches its critical threshold within the first 12 to 24 hours. After imbibition, the embryo swells and the radicle โ€” the embryonic root โ€” pushes through the seed coat and begins to grow downward.

This radicle emergence requires both continued water supply and sufficient oxygen exchange in the surrounding soil. Root tip cells are dividing rapidly during this phase, and their metabolism is highly aerobic (oxygen-dependent). Compacted or poorly aerated soil impairs radicle elongation even without any chemical contamination involved.

Germinating seeds are also at peak biochemical vulnerability during this window. Their antioxidant defense systems have not yet fully activated, and any chemical stressors introduced during imbibition โ€” such as leached additives from nearby plastic particles โ€” enter cells that have not yet built the protective machinery to detoxify them. The germination stage is, in short, the period when a plant is least equipped to handle external threats and most dependent on precise physical and chemical soil conditions.

Lentils: Why This Crop Matters Globally

Lentils (Lens culinaris) are far more than just a humble pulse; they are a nutritional powerhouse and global economic staple. They pack an exceptional nutritional punch, being very high in protein (up to 30%), fiber, and complex carbohydrates. Furthermore, they are rich in essential amino acids (like lysine, often lacking in grains), vital minerals such as iron and folate, and beneficial fatty acids, all while being low in fat and calories.

This makes them incredibly important, especially in regions where meat is less accessible. Beyond basic nutrition, lentils offer proven health benefits. They help control

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  • blood sugar,
  • aiding diabetes management,
  • boost metabolism,
  • improve digestion,
  • reduce the risk of heart disease, and
  • may even offer some cancer-preventative properties.

Economically and as a food source, lentils are indispensable. They are a dietary cornerstone across West Asia, North Africa, and East Africa. Global production reached a massive 6.3 million tons in 2018, and demand is rising, with projections indicating it will hit 8.4 million tons by 2024.

Scientifically, lentils are also important. They are frequently used as a โ€œmodel organismโ€ in environmental toxicity studies because they are highly sensitive to pollutants and stressors, making them an excellent early warning system, which is why they were chosen for this critical microplastic research.

Four Mechanisms by Which Microplastics Block Lentil Seeds Sprouting

The damage microplastics inflict on germinating lentil seeds does not operate through a single pathway. Four distinct mechanisms work simultaneously, which is why the effects are difficult to reverse simply by improving one soil condition in isolation.

Physical Blockage of Soil Pores and Seed Channels

The landmark study by De Silva et al. (2022), published in Chemosphere, used polyethylene microplastics in the size range of 740 to 4,990 nanometers โ€” meaning particles between roughly 0.74 and 5 micrometers in diameter. This size range overlaps directly with the diameter of micropores in lentil seed coats, which range from approximately 4 to 8 micrometers.

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When microplastic particles accumulate on the seed surface or in nearby soil pores, they physically obstruct the channels through which water must flow during imbibition. The seed cannot absorb water fast enough to activate its enzymes, and germination stalls or proceeds at a severely reduced rate.

The same physical mechanism operates at the soil level. Microplastics that accumulate in soil macropores reduce the overall porosity of the soil matrix, decreasing water and oxygen movement through the root zone. A germinating seed depending on diffuse oxygen exchange through soil air pockets finds those pockets increasingly obstructed as particle concentration rises.

Chemical Leaching from Plastic Additives

Plastic is never chemically pure. As plastic particles age and fragment in soil, they release these additives into the surrounding soil water. Commercial plastics contain a range of additives including

  1. plasticizers (chemicals that make plastic flexible),
  2. UV stabilizers,
  3. colorants,
  4. antioxidants, and
  5. flame retardants.

A 2025 study published in the Journal of Ecology (Lozano et al.) confirmed that total organic carbon in water extracts from microplastics was measurably elevated compared to control water, demonstrating real-time leaching of organic contaminants. Bisphenol A (BPA), a well-characterized plasticizer, has been shown to negatively affect seedling growth when seeds are exposed to it at environmentally relevant concentrations, with effects intermediate between fresh and aged plastic leachate.

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For lentil seeds in the critical imbibition phase, leached additives enter seed cells through the same water uptake channels that the seed depends on for activation. Inside the embryo, these compounds can interfere with enzyme activation, disrupt membrane integrity, and generate oxidative stress โ€” a condition where reactive oxygen molecules damage cellular components faster than antioxidant defenses can neutralize them.

Changes to Soil Structure and Microbial Communities

Soil around a germinating seed is not simply an inert medium. It hosts a dense community of bacteria and fungi whose activity supplies soluble nutrients to the emerging root and maintains the chemical conditions that support growth. Microplastics alter this community in measurable ways. Research cited in Frontiers in Plant Science (2025) found that bacterial and fungal diversity on microplastic surfaces is distinctly lower and different from the bulk soil microbiome.

Fungal diversity shows a particularly strong response, declining in both species richness and functional diversity as microplastic concentration increases. The loss of beneficial mycorrhizal fungi โ€” root-associated fungi that supply phosphorus and water in exchange for carbon from the plant โ€” removes a key support system just when a germinating seedling needs it most.

Additionally, microplastics alter soil physical properties including bulk density and pore size distribution, reducing the moisture-holding capacity that a germinating seed depends on to maintain continuous water supply through the imbibition phase. As a 2024 study in PNAS Nexus confirmed, even low levels of plastic accumulation on farms negatively correlated with soil moisture, microbial activity, available phosphate, and soil carbon pool size โ€” all parameters that directly influence germination success.

Oxidative Stress and Enzymatic Disruption Inside the Seed

Seeds under microplastic stress mount a measurable biochemical defense response. Antioxidant enzymes such as catalase and peroxidase activate to neutralize reactive oxygen species generated by chemical stressors. This is not a harmless adaptation โ€” activating antioxidant defenses draws on the seedโ€™s stored metabolic energy, reducing the resources available for radicle elongation and early cell division.

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The De Silva et al. study measured antioxidant enzyme activity alongside germination metrics and found that stressed seeds were expending resources on detoxification rather than growth, contributing to reduced seedling weight and root length even in seeds that technically germinated.

De Silva YSK, Rajagopalan UM, Kadono H, and Li D (2022, Chemosphere) found that polyethylene microplastics at concentrations of 10, 50, and 100 mg/L produced statistically significant reductions in lentil seed internal biological activity within just 6 hours of exposure, detectable only with biospeckle optical coherence tomography (bOCT) before any visible germination changes appeared.

Damage to germinating lentil seeds begins in the first working day of exposure โ€” well before a farmer would notice any field-level symptom, making conventional scouting methods inadequate for early detection.

Observed Effects on Lentil Seed Growth

When microplastic effects on lentil seeds accumulate past the invisible biochemical stage, they produce measurable changes across every metric of germination and early seedling performance. The dose-dependent pattern โ€” meaning worse outcomes at higher concentrations โ€” is consistent across multiple studies and gives researchers high confidence that the relationship is causal, not coincidental. Four categories of measurable damage emerge clearly from the experimental literature:

1. Reduced germination rate: At realistic field concentrations, microplastic exposure cuts overall germination percentage significantly. Research compiled in a systematic review published in Science of the Total Environment (Zantis et al., 2023) confirmed that nano- and microplastics commonly cause adverse impacts on plants at environmentally relevant levels, with germination rate reductions documented across multiple crop species including legumes.

2. Delayed sprouting time: Seeds that do germinate take longer to complete the process under microplastic stress. Delayed germination is agronomically damaging because it creates uneven crop emergence, makes crops more vulnerable to early-season weeds and pests, and shortens the effective growing season in environments with defined rainfall windows or frost dates.

3. Weak and abnormal root development: The radicle, the first root structure to emerge, shows reduced length and abnormal morphology in microplastic-exposed lentil seeds. Root shortening of approximately 50% has been reported at realistic microplastic concentrations (Cultivation Ag review, 2025), with associated reductions in root surface area that limit the plantโ€™s ability to acquire water and nutrients even after germination succeeds.

4. Lower seedling vigor and survival rate: Fresh and dry seedling weight โ€” standard measures of early plant vigor โ€” decrease in proportion to microplastic concentration. Seeds that germinate under heavy microplastic stress produce weaker seedlings that are more likely to die before establishing as productive plants, reducing final stand density even when the initial germination percentage appears adequate.

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The reductions in shoot growth are particularly severe. Some experimental results suggest shoot length suppression of approximately 70% at 100 mg/L concentrations โ€” a level that, while higher than typical ambient field conditions, is within the range possible in heavily mulched soils or fields receiving continuous plastic input over many years.

Zantis LJ, Borchi C, Vijver MG, Peijnenburg W, Di Lonardo S, and Bosker T (Science of the Total Environment, 2023) found in a systematic review of the literature that nano- and microplastics commonly cause adverse impacts on plants at environmentally relevant levels, with negative effects on germination, root elongation, and biomass accumulation documented across a broad range of crop and non-crop species. Microplastic effects on germination are not a laboratory curiosity confined to extreme concentrations โ€” they occur at concentration levels already present in contaminated agricultural fields worldwide.

How Germination Damage Scales Up

What happens at the level of one lentil seed translates directly into field-scale, regional-scale, and ultimately food-system-scale consequences. Understanding this scaling is important because farm-level decisions about plastic use are made in an economic context, and the true cost of that plastic use needs to include downstream agricultural losses.

Reduced germination rates translate directly into lower plant populations per hectare. In lentil production, optimal plant density is critical for yield, because lentil plants do not compensate well for low populations by producing extra pods or seeds on individual plants. A germination reduction of 20 to 40 percent, which is within the range documented at realistic microplastic exposure levels, can translate to proportional yield losses without any other stress factor involved.

The true cost of plastic in agriculture is not paid at the time of purchase. It is paid across generations of degraded soil, suppressed germination, and declining crop yields โ€” costs that fall hardest on the farmers and communities least equipped to absorb them.

Soil fertility itself degrades under sustained microplastic accumulation. The disruption of beneficial soil bacteria and fungi โ€” including nitrogen-fixing bacteria that are especially important for legumes like lentils โ€” means that the natural fertility inputs these organisms provide decline over time. Lentils are valued partly because they fix atmospheric nitrogen through their root nodules, reducing the need for synthetic nitrogen fertilizer.

This nitrogen fixation depends entirely on the activity of Rhizobium bacteria in the root zone. Microplastic-driven shifts in soil microbial communities threaten to undermine this process, potentially turning a nitrogen-fixing crop into one that demands added nitrogen to achieve normal yields.

At the food security level, lentils are not a marginal crop. Global lentil production has been climbing steadily toward the 8.4 million ton projection for 2024 cited in research literature, serving as a dietary protein foundation for populations across South Asia, North Africa, and East Africa. Systematic suppression of germination rates across the lentil-growing regions of these continents โ€” regions where plastic mulch use and irrigation with contaminated water are increasing โ€” represents a real and compounding threat to both farm income and regional food access.

What the Science Says: Key Experiments and Their Findings

The scientific case against microplastics in germination zones has been built through a convergence of laboratory bioassays, field surveys, and increasingly sophisticated optical imaging techniques. Looking at this evidence together gives a clearer picture of both what we know and what still requires investigation.

The most technically significant study on lentils specifically used biospeckle optical coherence tomography (bOCT) โ€” a non-destructive imaging technique that detects internal biological activity in plant tissue by measuring the coherent scattering pattern of infrared laser light reflected from within the seed.

Traditional germination assessments require waiting several days and then destroying the seed to measure it. bOCT detects changes in internal cellular movement within hours, without disturbing the seed. De Silva et al. (2022) used this technique to show that polyethylene microplastics (740 to 4,990 nm particle size) produced statistically significant reductions in lentil seed internal activity after just 6 hours.

Critically, conventional measurements โ€” germination viability, root length, shoot length โ€” showed no significant effect until at least 2 days of exposure. This gap between hidden damage and visible symptoms is exactly why microplastic contamination is so difficult to detect in normal farming practice.

Research on other legume species supports the lentil findings. A 2024 study published in Toxics (Su et al.) examined nanoplastic effects on soybean and mung bean and found species-specific differences in growth toxicity, confirming that legumes as a group are sensitive to plastic particle exposure but respond with different thresholds and mechanisms depending on the species.

A broader review published by Frontiers in Plant Science in August 2025 confirmed that microplastics at environmentally relevant concentrations disrupt growth and stress pathways in edible crops through species-specific mechanisms, with physical obstruction of root elongation specifically documented in lentil as one of the key pathways.

Dose-dependent effects appear consistently across the lentil research. Higher concentrations of microplastics produce worse outcomes, not in a linear pattern but in a threshold pattern โ€” low concentrations (10 mg/L) produce detectable biochemical changes, moderate concentrations (50 mg/L) produce measurable germination delays and root shortening, and high concentrations (100 mg/L) produce severe suppression of both germination rate and seedling biomass.

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The critical practical question for farmers and agronomists is where real agricultural soils sit on this concentration gradient, and the answer from field surveys is: it varies widely, with heavily mulched or repeatedly irrigated soils potentially reaching concerning concentrations.

What Farmers, Researchers, and Policymakers Can Do

Addressing microplastic contamination in agricultural soils requires action at multiple levels simultaneously. No single intervention is sufficient on its own, but together they form a viable pathway toward reducing harm.

Reducing Plastic Input at the Source

The most effective long-term strategy is preventing plastic from entering the soil in the first place. Practical measures include:

i. Transitioning to biodegradable mulch films made from certified compostable polymers such as PBAT (polybutylene adipate terephthalate) or PLA (polylactic acid). These materials break down into carbon dioxide, water, and biomass under soil conditions, rather than fragmenting into persistent microplastics.

Research by Bitton, Zucker, and Gruntman (Science of the Total Environment, 2025) confirmed that microplastic exposure reduces seed germination in coastal plants, reinforcing the urgency of switching to non-persistent alternatives wherever possible.

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ii. Replacing single-use plastic mulch with reusable mechanical weed suppression systems, cover cropping strategies, or organic mulches such as straw or wood chip where crops and climate conditions allow.

iii. Treating irrigation water before field application to reduce the particle load delivered with each watering cycle, particularly in areas drawing from surface water bodies known to carry urban or industrial plastic contamination.

Soil Remediation Approaches

For soils already contaminated, several remediation strategies have been studied with varying degrees of practical applicability:

  1. Thermal treatment at temperatures above the melting point of common plastic polymers destroys microplastics in soil but is energetically expensive and disrupts beneficial soil organisms, making it suitable only for severely contaminated plots with high economic value.
  2. Bioremediation using plastic-degrading microorganisms is an active research area. Certain bacterial strains can metabolize polyethylene and polypropylene, though current degradation rates are too slow for practical field application without significant further development.
  3. Phytoremediation, the use of plants to extract or bind contaminants, has shown some promise with heavy metals and organic pollutants but has limited direct application to solid plastic particles, which cannot be absorbed through plant roots in the way soluble contaminants can.
  4. Soil organic matter additions through compost, biochar, or cover cropping do not remove microplastics but improve soil structure, moisture retention, and microbial diversity in ways that partially offset the functional damage microplastics cause, supporting better germination conditions even in contaminated soils.

Policy and Waste Management Reform

Regulatory frameworks are beginning to catch up with the science. Indiaโ€™s Plastic Waste Management Rules, extended producer responsibility frameworks in the European Union, and the United Nations Global Plastics Treaty negotiations all reflect growing recognition that plastic use in agriculture needs stricter oversight.

Effective policies would include extended producer responsibility for agricultural plastic films, mandatory collection and recycling programs for plastic mulch, standards for microplastic content in sewage sludge applied to food-producing land, and labeling requirements that help farmers compare the true lifecycle impacts of conventional and biodegradable mulch products.

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Without policy intervention, the economic incentive structure of cheap single-use plastic will continue to drive soil contamination faster than voluntary adoption of alternatives.

Conclusion

Microplastics stunt lentil seeds before they even sprout through a set of mechanisms that are now well-documented but still insufficiently acted upon. Physical blockage of soil pores and seed coat channels limits water uptake during the critical imbibition phase. Chemical leaching from plastic additives introduces toxic compounds into embryonic cells that have not yet developed full detoxification capacity. Disruption of soil microbial communities removes the biological support network that germinating seeds depend on for nutrient supply and soil condition. And oxidative stress within the seed itself diverts metabolic energy from growth to detoxification, producing weaker seedlings with compromised root systems even when germination appears to succeed.

The cumulative result โ€” reduced germination rates, delayed sprouting, stunted roots, and lower seedling vigor โ€” translates directly into lost yield, degraded soil fertility, and threatened food security in regions where lentils are a nutritional cornerstone. The concentration levels at which these effects occur are not extreme laboratory scenarios. They overlap with concentrations already measured in agricultural fields that have used plastic mulch for multiple seasons or receive irrigation water from contaminated sources. Addressing how microplastics stunt lentil seeds requires honest acknowledgment that the convenience of plastic in modern farming comes with long-term biological costs that accumulate invisibly in the soil.

Frequently Asked Questions (FAQs)

What is Polyethylene Microplastics (PEMPs):ย Microplastics specifically made from polyethylene plastic. Polyethylene is common in plastic bags and mulch films. They are important in this study as the pollutant tested on lentils, showing how this specific plastic type physically blocks seed pores and hinders growth. The sizes tested ranged from 740 to 4990 nanometers.

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What is Biospeckle Optical Coherence Tomography (bOCT):ย A special imaging technique combining light scattering (biospeckle) and deep imaging (OCT). It non-destructively measures internal movement and activityย insideย living things like seeds. Itโ€™s important here because it detected reduced activity in lentils caused by PEMPs within just 6 hours, much faster than conventional methods. Formula: Contrastย r(x,y) = ฯƒ / <I>ย (Standard Deviation of Intensity / Mean Intensity over time).

What is Biospeckle:ย The grainy, flickering light pattern seen when laser light shines on a living biological sample. The flickering is caused by tiny internal movements like water flow or cell activity. Itโ€™s important because it acts as a โ€œbioindicatorโ€; measuring its intensity (contrast) shows how active the tissue is inside the seed.

What is Dose-Dependent Effect:ย When the impact of something (like a pollutant) gets stronger or weaker as its amount (dose) increases or decreases. Itโ€™s important for proving cause-and-effect and understanding toxicity levels. This study clearly showed this: higher PEMP concentrations caused greater reductions in bOCT contrast, germination rates, and seedling growth.

What is Reactive Oxygen Species (ROS):ย Chemically reactive molecules containing oxygen (like hydrogen peroxide โ€“ Hโ‚‚Oโ‚‚), naturally produced during metabolism but can surge under stress, damaging cells. They are important markers of plant stress. The study found increased Hโ‚‚Oโ‚‚ levels in PEMP-exposed lentils, signaling stress.

What is Region of Interest (ROI):ย A specific area selected within an image or dataset for focused analysis. It allows precise measurement. In bOCT analysis, ROIs were chosen inside the lentil seed (between coat and cotyledon) to calculate the average local speckle contrast, avoiding surface artifacts.

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What is Average Local Contrast (ALC):ย The mean value of the biospeckle contrast calculated within a specific Region of Interest (ROI) inside the seed image. It quantifies the activity level in that specific part. Six ROIs per seed image were analyzed to get this value.

References:

1. De Silva, Y. S. K., Rajagopalan, U. M., Kadono, H., & Li, D. (2022). Effects of microplastics on lentil (Lens culinaris) seed germination and seedling growth. Chemosphere, 303, 135162.

2. De Silva, Y. S. K., Rajagopalan, U. M., Kadono, H., & Li, D. (2023). The synergy of microplastics with the heavy metal zinc has resulted in reducing the toxic effects of zinc on lentil (Lens culinaris) seed germination and seedling growth. Heliyon, 9(11).

3. Lozano, Y. M., Caesaria, P. U., & Rillig, M. C. (2022). Microplastics of different shapes increase seed germination synchrony while only films and fibers affect seed germination velocity. Frontiers in Environmental Science, 10, 1017349.

4. Dawood, M. F., Hamed, H. A., & El-Mahdy, M. T. (2025). Impact of Microplastics and Nanoplastics on Plant Health and Development. In Microplastics Pollution: A Threat to Biosphere (pp. 113-153). Cham: Springer Nature Switzerland.

5. Naqash, N., Yadav, K. K., Shaik, A. S., Alam, M. W., Djajadi, D., Sunarto, D. A., โ€ฆ & Wani, A. K. (2025). Microplastic pollution in terrestrial systems: Sources and implications for soil functioning and plant performance. Water, Air, & Soil Pollution, 236(3), 172.

6. Basumatary, T., Dey, R., Nava, A. R., Irnidayanti, Y., Narayan, M., & Sarma, H. (2026). Micro, nano, and biodegradable plastics: hidden threats to plant health and soil function. Reviews of Environmental Contamination and Toxicology, 264(1), 2.

7. Tyagi, L., Kadono, H., & Rajagopalan, U. M. (2026). Synergistic effects of titanium dioxide nanoparticles and microplastics on lentil seeds by a non-invasive biospeckle optical coherence tomography. Frontiers in Plant Science, 17, 1718010.

8. De Silva, Y. S. K., Rajagopalan, U. M., & Kadono, H. (2023, May). Biospeckle optical coherence tomography reveals the mitigation of the harmful effects of heavy metal zinc in combination with polyethylene microplastics in lentil seeds. In SPIE Future Sensing Technologies 2023 (Vol. 12327, pp. 129-136). SPIE.

9. Spanรฒ, C., Giorgetti, L., Bottega, S., Muccifora, S., & Ruffini Castiglione, M. (2024). Titanium dioxide nanoparticles enhance the detrimental effect of polystyrene nanoplastics on cell and plant physiology of Vicia lens (L.) Coss. & Germ. seedlings. Frontiers in Plant Science, 15, 1391751.

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