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Research article · 2025 · Full text

International Journal of Biology Sciences

Microplastic ingestion and physiological effects on filter-feeding bivalve mollusks

Lisette CharbonneauKnox Frechette

Volume 7(12) · Pages 135–138 · DOI: 10.33545/26649926.2025.v7.i12b.677 ↗

Research areasMicroplastics and Plastic PollutionEnvironmental Toxicology and EcotoxicologyMarine Ecology and Invasive Species

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Abstract

Author-written

Marine microplastic pollution is no longer a distant threat—it is already reshaping the physiology of organisms at the base of coastal food webs. This research exposed three species of filter-feeding bivalves (Mytilus edulis, Crassostrea gigas, and Venerupis philippinarum) to polyethylene microplastic particles (10–300 µm) at concentrations ranging from 10 to 5,000 particles per liter over a 28-day period. Filtration rate declined in a dose-dependent manner across all species, with M. edulis showing the sharpest reduction (85.4% at 5,000 particles/L). Histological examination revealed epithelial inflammation in gill tissues and particle accumulation in digestive glands. These findings demonstrate that environmentally relevant microplastic concentrations can impair core physiological functions in commercially important bivalve species.

Summary

Source-checked

Plain-language reading of the full paper, prepared with AI and checked against the text. Each point links to the authors' own words.

  1. Why it matters

    • Marine microplastic pollution is a growing global issue, with an estimated 13,000 to 18,000 fragments per square kilometer of ocean surface. View evidence ↗

      Why it matters

      Marine microplastic pollution is a growing global issue, with an estimated 13,000 to 18,000 fragments per square kilometer of ocean surface.

      In the paper's own words

      “Every square kilometer of ocean surface now contains an estimated 13,000 to 18,000 microplastic fragments, and that number keeps rising [1].”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • Filter-feeding bivalves are highly susceptible to microplastics because their gill-based feeding mechanism makes it hard to distinguish these particles from food. View evidence ↗

      Why it matters

      Filter-feeding bivalves are highly susceptible to microplastics because their gill-based feeding mechanism makes it hard to distinguish these particles from food.

      In the paper's own words

      “Filter-feeding bivalves are particularly vulnerable because their feeding mechanism—drawing large volumes of water across ciliated gill surfaces—makes particle discrimination difficult once items fall within the ingestible size range [2].”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • A decline in filtration rate is a critical physiological marker because it leads to decreased food intake, which can eventually reduce growth and reproduction. View evidence ↗

      Why it matters

      A decline in filtration rate is a critical physiological marker because it leads to decreased food intake, which can eventually reduce growth and reproduction.

      In the paper's own words

      “Reductions in filtration rate translate directly into lower food intake and, over time, reduced growth and reproductive output [5].”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
  2. The question

    • The study aimed to determine how exposure to various concentrations of polyethylene microplastics over 28 days affects the filtration rate, tissue accumulation, and histology of three commercial bivalve species. View evidence ↗

      The question

      The study aimed to determine how exposure to various concentrations of polyethylene microplastics over 28 days affects the filtration rate, tissue accumulation, and histology of three commercial bivalve species.

      In the paper's own words

      “This research exposed three commercially harvested bivalve species to a range of polyethylene microplastic concentrations for 28 days and measured filtration rate, tissue accumulation, and histological changes”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
  3. What they did

    • The experiment used 120 adult specimens each of Mytilus edulis, Crassostrea gigas, and Venerupis philippinarum collected from British Columbia. View evidence ↗

      What they did

      The experiment used 120 adult specimens each of Mytilus edulis, Crassostrea gigas, and Venerupis philippinarum collected from British Columbia.

      In the paper's own words

      “Adult specimens of M. edulis (n=120), C. gigas (n=120), and V. philippinarum (n=120) were collected from Esquimalt Lagoon, British Columbia, in April 2023”

      Page 1

      Found in: Material

      Read it in the full textOpen PDF at page 1 ↗
    • Animals were divided into treatment groups exposed to polyethylene microplastic concentrations of 0, 10, 50, 100, 500, 1,000, and 5,000 particles per liter, with 15 individuals per species in each group. View evidence ↗

      What they did

      Animals were divided into treatment groups exposed to polyethylene microplastic concentrations of 0, 10, 50, 100, 500, 1,000, and 5,000 particles per liter, with 15 individuals per species in each group.

      In the paper's own words

      “Bivalves were randomly assigned to six treatment groups (0, 10, 50, 100, 500, 1,000, and 5,000 particles/L) with 15 individuals per species per treatment.”

      Page 2

      Found in: Methods

      Read it in the full textOpen PDF at page 2 ↗
    • Filtration rates were assessed weekly using the clearance rate method with the alga Isochrysis galbana. View evidence ↗

      What they did

      Filtration rates were assessed weekly using the clearance rate method with the alga Isochrysis galbana.

      In the paper's own words

      “Filtration rate was measured weekly using a clearance rate method with Isochrysis galbana as the food alga [4].”

      Page 2

      Found in: Methods

      Read it in the full textOpen PDF at page 2 ↗
    • On the 28th day, five animals per group underwent histological examination of the digestive glands and gills using 5 µm sections stained with H&E. View evidence ↗

      What they did

      On the 28th day, five animals per group underwent histological examination of the digestive glands and gills using 5 µm sections stained with H&E.

      In the paper's own words

      “At day 28, five animals per group were sacrificed for histological analysis of gill and digestive gland tissues. Sections (5 µm) were stained with H&E and examined under light microscopy.”

      Page 2

      Found in: Methods

      Read it in the full textOpen PDF at page 2 ↗
  4. What they found

    • All three bivalve species experienced a significant, dose-dependent decrease in their filtration rates (p < 0.001). View evidence ↗

      What they found

      All three bivalve species experienced a significant, dose-dependent decrease in their filtration rates (p < 0.001).

      In the paper's own words

      “All three species showed significant dose-dependent reductions in filtration rate (p < 0.001).”

      Page 2

      Found in: Results

      Read it in the full textOpen PDF at page 2 ↗
    • Histological analysis showed that microplastics accumulated in the digestive glands and caused inflammation in the gill epithelia. View evidence ↗

      What they found

      Histological analysis showed that microplastics accumulated in the digestive glands and caused inflammation in the gill epithelia.

      In the paper's own words

      “Histological examination revealed epithelial inflammation in gill tissues and particle accumulation in digestive glands.”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • At concentrations typical of coastal waters (100 particles/L), filtration rates decreased by 17% to 27% across the species. View evidence ↗

      What they found

      At concentrations typical of coastal waters (100 particles/L), filtration rates decreased by 17% to 27% across the species.

      In the paper's own words

      “Even at 100 particles/L, filtration rate dropped by 17–27% depending on species”

      Page 3

      Found in: Discussion

      Read it in the full textOpen PDF at page 3 ↗
  5. What it means

    • The authors conclude that existing coastal microplastic levels may be impairing bivalve feeding, which could negatively impact ecosystem services and aquaculture. View evidence ↗

      What it means

      The authors conclude that existing coastal microplastic levels may be impairing bivalve feeding, which could negatively impact ecosystem services and aquaculture.

      In the paper's own words

      “These results indicate that current coastal microplastic levels may already be affecting bivalve feeding performance, with potential consequences for aquaculture productivity and ecosystem filtration services.”

      Page 3

      Found in: Conclusion

      Read it in the full textOpen PDF at page 3 ↗
    • The study is limited by the use of pristine microspheres, noting that weathered or biofilm-coated particles might behave differently. View evidence ↗

      What it means

      The study is limited by the use of pristine microspheres, noting that weathered or biofilm-coated particles might behave differently.

      In the paper's own words

      “A limitation of this research is the use of pristine microspheres rather than weathered or biofilm-coated particles, which may behave differently during ingestion [11].”

      Page 3

      Found in: Discussion

      Read it in the full textOpen PDF at page 3 ↗

Visual summary

2 visuals

Illustrations explain the paper; charts are replotted from the paper's own table values.

AI-generated illustration
AI-generated conceptual illustration (Blue mussels (Mytilus edulis)). It explains the idea and does not show study data.↗ Enlarge
Microplastic Ingestion Pathway
AI-generated conceptual illustration (Blue mussels (Mytilus edulis)). It explains the idea and does not show study data.

AI-generated conceptual illustration (Blue mussels (Mytilus edulis)). It explains the idea and does not show study data.

Open full-size image ↗

Microplastic Ingestion Pathway

AI-generated conceptual illustration (Blue mussels (Mytilus edulis)). It explains the idea and does not show study data.

View source evidence ↗
Replotted from source data
Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.↗ Enlarge
0 p/L and 10 p/L and more: M. edulis vs C. gigas vs V. philippinarum
Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

Open full-size image ↗

0 p/L and 10 p/L and more: M. edulis vs C. gigas vs V. philippinarum

Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

View source evidence ↗

Figures & tables

From the original paper
Filtration Rate (L/h/g) After 28-Day Microplastic ExposureTable 1Page 2Relationship between microplastic concentration and filtration rate across all three bivalve species over the 28-day exposure period.Figure 1Page 2Schematic of microplastic ingestion pathway in filter-feeding bivalves, from water column capture through gill filtration to tissueFigure 2Page 3
FULL TEXT Original article · reflowed for reading

Introduction

Every square kilometer of ocean surface now contains an estimated 13,000 to 18,000 microplastic fragments, and that number keeps rising [1] . Filter-feeding bivalves are particularly vulnerable because their feeding mechanism-drawing large volumes of water across ciliated gill surfaces-makes particle discrimination difficult once items fall within the ingestible size range [2] . Earlier work has shown that bivalves can ingest microplastics, but the physiological consequences of sustained exposure remain less clear, particularly at concentrations matching field conditions [3] . Filtration rate is a sensitive endpoint because it integrates gill function, valve gaping behavior, and energetic balance into a single measurable output [4] . Reductions in filtration rate translate directly into lower food intake and, over time, reduced growth and reproductive output [5] . This research exposed three commercially harvested bivalve species to a range of polyethylene microplastic concentrations for 28 days and measured filtration rate, tissue accumulation, and histological changes at the Pacific Institute of Marine Biology, Victoria, Canada [6] .

Reagents and Chemicals

Polyethylene microspheres (10-300 µm, density 0.96 g/cm³) were purchased from Cospheric LLC (Santa Barbara, CA, USA; Cat. No. CPMS-0.96). Nile Red fluorescent dye (Sigma-Aldrich, Cat. No. 72485) was used to stain particles for visualization. Bouin's fixative (Sigma-Aldrich, Cat. No. HT10132) and hematoxylin-eosin staining reagents (Thermo Fisher Scientific) were used for histological preparation. Filtered seawater (0.45 µm) served as the exposure medium.

Material and Methods

Material and Methods

Material

Adult specimens of M. edulis (n=120), C. gigas (n=120), and V. philippinarum (n=120) were collected from Esquimalt Lagoon, British Columbia, in April 2023 and acclimated for 14 days at the Pacific Institute of Marine Biology. Animals were held in aerated, filtered seawater at 13±0. 5

Methods

Bivalves were randomly assigned to six treatment groups (0, 10, 50, 100, 500, 1,000, and 5,000 particles/L) with 15 individuals per species per treatment. Exposure ran for 28 days with full water renewal every 48 hours. Filtration rate was measured weekly using a clearance rate method with Isochrysis galbana as the food alga [4] . At day 28, five animals per group were sacrificed for histological analysis of gill and digestive gland tissues. Sections (5 µm) were stained with H&E and examined under light microscopy. Microplastic burden in soft tissues was quantified after KOH digestion and vacuum filtration, with Nile Red fluorescence counting [7] . Data were analyzed using twoway ANOVA (species × concentration) with Tukey's HSD post-hoc test.

Quality Control

Procedural blanks were processed alongside every batch of tissue digestions to monitor airborne microplastic contamination. All labware was rinsed three times with filtered deionized water. Cotton laboratory coats were worn to reduce fiber shedding. Particle counts in blanks averaged 0.8±0.4 particles per sample and were subtracted from tissue counts.

Results

Table All three species showed significant dose-dependent reductions in filtration rate (p < 0.001). M. edulis was the most sensitive, losing 85.4% of baseline filtration at the highest concentration.

Discussion

The dose-dependent decline in filtration rate observed here matches patterns reported for M. edulis exposed to polystyrene beads [3] , but extends the finding to two additional species and to polyethylene-the most abundant polymer type in marine environments [8] . Histological changes in gill epithelia suggest that physical irritation from particle contact may trigger mucus overproduction, clogging the filtration apparatus and forcing valve closure [9] . The concentrations used in this research span both environmentally relevant levels (10-100 particles/L, typical of coastal waters [10] ) and elevated levels representing pollution hotspots. Even at 100 particles/L, filtration rate dropped by 17-27% depending on species-a reduction that, if sustained, could impair energy budgets over a reproductive season [5] . A limitation of this research is the use of pristine microspheres rather than weathered or biofilm-coated particles, which may behave differently during ingestion [11] .

Conclusion

This research demonstrated that polyethylene microplastic exposure at concentrations ranging from 10 to 5,000 particles per liter significantly reduced filtration rates in three commercially important bivalve species over 28 days. M. edulis was the most sensitive species, while C. gigas showed moderate tolerance at lower concentrations. Gill histopathology confirmed physical tissue damage at higher exposure levels. These results indicate that current coastal microplastic levels may already be affecting bivalve feeding performance, with potential consequences for aquaculture productivity and ecosystem filtration services.

Acknowledgement

Acknowledgements Funding SourcesThis research was supported by the Pacific Institute of Marine Biology internal research fund. Institutional SupportThe authors thank the Department of Marine Ecology for laboratory and mesocosm facilities. Contributions Not Qualifying for AuthorshipField collection was assisted by graduate students in the Marine Invertebrate Ecology program.

Figures and tables from the paper

Table 1. Filtration Rate (L/h/g) After 28-Day Microplastic Exposure
Species0 p/L10 p/L100 p/L500 p/L1000 p/L5000 p/L
M. edulis4.81±0.314.58±0.283.52±0.412.31±0.381.42±0.290.70±0.22
C. gigas3.94±0.273.81±0.333.19±0.292.47±0.421.83±0.311.12±0.26
V. philippinarum3.12±0.242.98±0.212.61±0.321.87±0.281.24±0.230.83±0.19

Table text extracted from the original PDF; superscript letters are shown inline. The original table image is below.

View original table image
Filtration Rate (L/h/g) After 28-Day Microplastic Exposure↗ Enlarge
Table 1
Filtration Rate (L/h/g) After 28-Day Microplastic Exposure

Filtration Rate (L/h/g) After 28-Day Microplastic Exposure

Open full-size image ↗
Original paper tableSource PDF · page 2 ↗
Figure 1. Relationship between microplastic concentration and filtration rate across all three bivalve species over the 28-day exposure period.
Relationship between microplastic concentration and filtration rate across all three bivalve species over the 28-day exposure period.↗ Enlarge
Figure 1
Relationship between microplastic concentration and filtration rate across all three bivalve species over the 28-day exposure period.

Relationship between microplastic concentration and filtration rate across all three bivalve species over the 28-day exposure period.

Open full-size image ↗
Original paper figureSource PDF · page 2 ↗
Figure 2. Schematic of microplastic ingestion pathway in filter-feeding bivalves, from water column capture through gill filtration to tissue
Schematic of microplastic ingestion pathway in filter-feeding bivalves, from water column capture through gill filtration to tissue↗ Enlarge
Figure 2
Schematic of microplastic ingestion pathway in filter-feeding bivalves, from water column capture through gill filtration to tissue

Schematic of microplastic ingestion pathway in filter-feeding bivalves, from water column capture through gill filtration to tissue

Open full-size image ↗
Original paper figureSource PDF · page 3 ↗

References

14 in the original paper
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