Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2025 Apr 29;20(4):e0319165.
doi: 10.1371/journal.pone.0319165. eCollection 2025.

Exposure to plastic debris alters expression of biomineralization, immune, and stress-related genes in the eastern oyster (Crassostrea virginica)

Affiliations

Exposure to plastic debris alters expression of biomineralization, immune, and stress-related genes in the eastern oyster (Crassostrea virginica)

Laura E Eierman et al. PLoS One. .

Abstract

The degradation of marine plastic debris poses a threat to organisms by fragmenting into micro- and nano-scale pieces and releasing a complex chemical leachate into the water. Numerous studies have investigated harms from plastic pollution such as microplastic ingestion and exposure to single chemicals. However, few studies have examined the holistic threat of plastic exposure and the synergistic impacts of chemical mixtures. The objective of this study was to measure changes in gene expression of gill and gonadal tissue of the eastern oyster (Crassostrea virginica) in response to plastic debris exposure during their first year, using RNA-seq to explore multiple types of physiological responses. Shell and polyethylene terephthalate plastic were used as substrate for the metamorphosis of larval oysters in a settlement tank. Substrate pieces were then transferred to metal cages and outplanted in pairs - shell cage and plastic cage - onto restoration reefs in the St. Mary's River, Maryland, USA. After 10 months of growth, the oysters were collected, gill and gonadal tissue removed, and sex identified. The tissues of six oysters from each sex and substrate type were then analyzed in RNA-seq. Both gill and gonadal tissue samples had altered expression of immune and stress-response genes in response to plastic exposure. Genes upregulated in response to plastic were enriched for gene ontology functions of proteolysis and fibrinolysis. Downregulated genes were involved in shell biomineralization and growth. One male oyster exposed to plastic had "feminized" gene expression patterns despite developing mature sperm, suggesting plastic leachate can alter gene expression and shift protandric individuals to develop as females. Plastic pollution may therefore reduce shell growth, initiate immune and stress responses, alter sex differentiation, and impact reproductive output of eastern oysters through changes in transcription.

PubMed Disclaimer

Conflict of interest statement

The authors have declared that no competing interests exist.

Figures

Fig 1
Fig 1. Venn diagrams of differentially expressed genes by model factor in each tissue.
Venn diagrams indicating the number of reference genes differentially expressed in response to model factors sex, substrate, and sex-by-substrate for (A) gill tissue, (B) gonad tissue, and (C) gonad tissue after the removal of the P8 male on plastic sample.
Fig 2
Fig 2. Multidimensional scaling plots of samples for each tissue.
Multidimensional scaling plots indicating the clustering of female and male samples on shell and plastic substrate based on patterns of read counts in all expressed genes for (A) gill tissue, (B) gonad tissue, and (C) gonad tissue after the removal of the P8 male on plastic sample.
Fig 3
Fig 3. Volcano plots of genes expressed in gill tissue by model factor.
Volcano plot log2 fold change in expression and false discovery rate of reference genes (n = 41,899) expressed in gill tissue in response to model factors (A) sex, (B) substrate, and (C) sex-by-substrate with differentially expressed genes indicated in red and a subset of genes labeled with gene annotation.
Fig 4
Fig 4. Volcano plots of genes expressed in gonad tissue by model factor.
Volcano plot log2 fold change in expression and false discovery rate of reference genes expressed in gonad tissue (n = 35,736) in response to model factors (A) sex, (B) substrate, and (C) sex-by-substrate and in gonad tissue after the removal of male on plastic sample P8 (n = 37,676) in response to model factors: (D) sex, (E) substrate, and (F) sex-by-substrate with differentially expressed genes indicated in red and a subset of genes labeled with gene annotation.
Fig 5
Fig 5. Enriched gene ontology terms of differentially expressed genes in gonadal tissue by sex.
Enriched gene ontology terms for genes differentially expressed in gonadal tissues indicating the number of genes and the false discovery rate of each term for (A) males, (B) males after the removal of male on plastic P8, and (C) females after the removal of male on plastic P8.
Fig 6
Fig 6. Enriched gene ontology terms of differentially expressed genes in gonadal tissue by plastic.
Enriched gene ontology terms for genes differentially expressed in gonadal tissues indicating the number of genes and the false discovery rate of each term for (A) oysters on plastic and (B) oysters on plastic after the removal of male on plastic P8.
Fig 7
Fig 7. Model results for twenty-four genes differentially expressed in both gill and gonadal tissue.
Model results for each of three factors (Sex, Substrate, and Sex-by-substrate) for twenty-four genes differentially expressed in both gill and gonadal tissue. For genes with differential expression for a model factor, the log fold change is provided. The sex factor indicates male expression relative to female ( + male/- female). The substrate factor indicates shell expression relative to plastic ( + shell/- plastic). The sex-by-substrate (SExSU) factor indicates male on shell expression relative to all other groups. Heat map colors are red for positive log-fold changes and blue for negative log-fold changes. Non-significant factors for a gene are indicated as 0 log-fold change.

Similar articles

References

    1. Colton JB Jr, Burns BR, Knapp FD. Plastic particles in surface waters of the northwestern atlantic. Science. 1974;185(4150):491–7. doi: 10.1126/science.185.4150.491 - DOI - PubMed
    1. Cózar A, Echevarría F, González-Gordillo JI, Irigoien X, Ubeda B, Hernández-León S, et al.. Plastic debris in the open ocean. Proc Natl Acad Sci U S A. 2014;111(28):10239–44. doi: 10.1073/pnas.1314705111 - DOI - PMC - PubMed
    1. Eriksen M, Lebreton LCM, Carson HS, Thiel M, Moore CJ, Borerro JC, et al.. Plastic Pollution in the World’s Oceans: More than 5 Trillion Plastic Pieces Weighing over 250,000 Tons Afloat at Sea. PLoS One. 2014;9(12):e111913. doi: 10.1371/journal.pone.0111913 - DOI - PMC - PubMed
    1. Goldstein MC, Titmus AJ, Ford M. Scales of Spatial Heterogeneity of Plastic Marine Debris in the Northeast Pacific Ocean. PLoS ONE. 2013;8(11):e80020. doi: 10.1371/journal.pone.0080020 - DOI - PMC - PubMed
    1. Law KL, Morét-Ferguson SE, Goodwin DS, Zettler ER, Deforce E, Kukulka T, et al.. Distribution of surface plastic debris in the eastern Pacific Ocean from an 11-year data set. Environ Sci Technol. 2014;48(9):4732–8. doi: 10.1021/es4053076 - DOI - PubMed

LinkOut - more resources