Elsevier

Chemosphere

Volume 283, November 2021, 131289
Chemosphere

Effects of PET microplastics on the physiology of Drosophila

https://doi.org/10.1016/j.chemosphere.2021.131289Get rights and content

Highlights

  • The higher the concentration of PET-MPs was, the more obvious impact on flies became.

  • PET-MPs increased the spontaneous activity of flies for 24 h.

  • PET-MPs reduced egg production in female flies.

  • PET-MPs decreased lipid, glucose content and starvation resistance in male flies.

Abstract

Microplastics, as a new type of pollution, have attracted global attention and have become a research focus in recent years. Given the small size of microplastics, they can be ingested by many organisms. In addition, microplastics can enter the human body through the food chain. So, the potential dangers of microplastics can't be ignored. This study took Drosophila as a model organism to delve the physiological effects of polyethylene terephthalate microplastics (PET-MPs). Here, we reported that the higher concentration of PET-MPs was, the more obvious the effect became. The amount of oviposition decreased in female flies exposed, indicating that microplastics affected reproduction. PET-MPs caused the decrease of triglyceride and glucose content in male flies, as well as the decrease of starvation resistance, suggesting the effect of microplastics on energy metabolism. In addition, the 24-h spontaneous activity of flies exposed to PET-MPs increased significantly. The experimental results can help understand the potential impact of microplastics on physiology.

Introduction

Microplastics are any polymeric matrix or synthetic solid particle, with size ranging from 1 μm to 5 mm and with regular or irregular shape (Frias and Nash, 2019). Plastic production is growing exponentially (Rochman et al., 2013). Since plastic is difficult to degrade, it will exist in the ecological environment in the form of microplastics for a long time after physical, chemical and biological actions. Microplastics pollution will become more and more serious. Tiny degradable plastic lurked in the oceans (Chubarenko et al., 2016), lakes (Xiong et al., 2018), soil (Rillig, 2012) and even in the air (Gasperi et al., 2018). Microplastics have also been found in drinking water (Koelmans et al., 2019), salt (Peixoto et al., 2019), seafood (Smith et al., 2018) and other foods. From plankton (Desforges et al., 2015) to earthworms (Rillig et al., 2017), from fish to humans, microplastics are consumed, causing a serious health threat to entire ecosystems.

Studies have shown that microplastics can be ingested by marine organisms, causing physical damage by blocking feeding auxiliary organs and digestive tracts. In addition, microplastics can also bring toxicological effects, such as oxidative damage (Lei et al., 2018b), increase of inflammation (Jin et al., 2018), decrease of immunity (Sharifinia et al., 2020), disorder in intestinal microorganism, hepatic metabolic disorders (Feng et al., 2021), fake fullness, decline in growth rate and increase in mortality (Jemec et al., 2016). Microplastics lead to decline in reproductive ability and has an impact on the production and development of offspring (Wang et al., 2019). In addition, the recent studies indicated that Polystyrene microplastics (PS-MPs) can cause inflammatory effects on human A549 lung cells and induce apoptosis in several human cell types, including human monocytic leukemia cell line (THP-1), human colon carcinoma cells (Caco-2), and human lung cancer cells (Calu-3) (Yee et al., 2021). Besides, microplastics have higher specific surface area than general plastics, and are easy to absorb organic pollutant such as perfluorinated compounds, fluorobenzene, aromatic hydrocarbons, polyfluorinated biphenyls, as well as substances such as heavy metals, bacteria and viruses, bringing mixed chemical pollution (Zhang et al., 2018; Verla et al., 2019). These contaminants are passed through the food chain and accumulate in living organisms, which may cause harmful effects on human health.

At present, the research on the harm of microplastics mostly focuses on two types, polyethylene (PE) or polystyrene (PS) (Lei et al., 2018a; Yin et al., 2018a; Enyoh et al., 2020; Malafaia et al., 2020; Matthews et al., 2021). There are few studies on other types of microplastics. In this experiment, Polyethylene terephthalate (PET) was chosen for research. PET is mainly used as packaging material and accounts for 7.1% of total plastic consumption in Europe. In addition, because of its high impact resistance, friction resistance and mechanical properties, it widely used in mineral water and carbonated beverage bottles. In the analysis of particles in the water, PET accounted for 84% in recyclable plastic bottles, and 31% in beverage bottles (Schymanski et al., 2018). An Austrian study shows that there are nine different types of microplastics found in human's feces, and the most common types are polyethylene terephthalate (PET) and polypropylene (PP) (Harvey and Watts, 2018). At the same time, 12 particles of microplastic were found in the placentas of 4 women (Ragusa et al., 2021). As a plastic type closely related to human life, the harm of the PET-MPs should not be overlooked.

In this experiment, Drosophila was selected as a biological model to explore whether PET-MPs would have an impact on physiology. The comparison of the genome sequences of Drosophila and human revealed a high degree of homology, which confirmed the feasibility and reliability of Drosophila as a model for the study of human diseases. It has been estimated that nearly 75% of human disease-related genes have functional direct-homologs in Drosophila. The results showed that PET-MPs increased the spontaneous activity of Drosophila (P < 0.01). PET-MPs decreased TG and glucose content in male flies (P < 0.05) and reduced the resistance to starvation in male flies (P < 0.05). PET-MPs reduced the amount of eggs laid (P < 0.05). In general, the experiment shows that the higher the concentration of PET-MPs was, the more obvious impact became on Drosophila.

Section snippets

The genotype, breeding of Drosophila and design of the experiment

In this experiment, Canton-S flies (Bloomington Drosophila Stock Center) were used. The emerging adults were collected within 24 h, and after 48 h for mating, the flies were divided into males and females. Flies were kept in an incubator with light/dark cycle for 12 h at the temperature of 25 °C, humidity of 60% and light intensity of 500 Lux. They were fed in sugar/yeast/agar medium. The flies were transferred to new vials every two days.

PET-MPs of 2 μm were used in this experiment. The

Effect of PET-MPs on the spontaneous activity

We investigated whether the spontaneous activity of Drosophila changes after exposed to PET-MPs. The experimental results showed that both male and female Drosophila have a significant increase in spontaneous activity after exposure to PET-MPs (P < 0.01) (Fig. 1A and B). According to the statistics, the 24 h total activity of female Drosophila with 1 g/L, 10 g/L and 20 g/L increased by 20%, 25% and 22% respectively, and that of male Drosophila increased by 28%, 32% and 43%, presenting an

Discussion

Our study found a significant increase in spontaneous activity in flies exposed to PET-MPs. The reason could be neuron damage. When the Caenorhabditis elegans were exposed to the PS-MPs, the crawling speed increased (Lei et al., 2018a). PS-MPS downregulated the expression of unc-47, dat-1, unc-17 in Caenorhabditis elegans resulting GABAergic neuron and cholinergic neuron damage, and this may cause the imbalance of excitation-inhibition process and exert excitatory effects (Lei et al., 2018a).

Compliance with ethical standards

The research was conducted on Drosophila melanogaster. The research complies with ethical standards.

Funding

This work was supported by the Grant from National Natural Science Foundation of China (31500970 to J.S.)

Ethical approval

Not applicable.

Informed consent

Not applicable.

Data availability statement

The authors confirm that the data supporting the findings of this study are available within the article.

Credit author statement

Jie Shen; Conceptualization, Supervision, Writing- Reviewing and Editing, Boying Liang; Project administration, Investigation, Formal analysis, Writing- Reviewing and Editing, Dake Zhang; Formal analysis, Reviewing and Editing, Yan Li; Investigation, Reviewing and Editing, Hao Tang; Reviewing and Editing, Lichao Zhong; Reviewing and Editing, Yifan Xu; Reviewing and Editing

Declaration of competing interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgements

This work was supported by the Grant from National Natural Science Foundation of China (31500970 to J.S.)

References (53)

  • L. Lu et al.

    Polystyrene microplastics induce gut microbiota dysbiosis and hepatic lipid metabolism disorder in mice

    Sci. Total Environ.

    (2018)
  • E.J. Park et al.

    Repeated-oral dose toxicity of polyethylene microplastics and the possible implications on reproduction and development of the next generation

    Toxicol. Lett.

    (2020)
  • D. Peixoto et al.

    Microplastic pollution in commercial salt for human consumption: a review. Estuarine

    Coast. Shelf Sci.

    (2019)
  • A. Ragusa et al.

    Plasticenta: first evidence of microplastics in human placenta

    Environ. Int.

    (2021)
  • D. Schymanski et al.

    Analysis of microplastics in water by micro-Raman spectroscopy: release of plastic particles from different packaging into mineral water

    Water Res.

    (2018)
  • M. Sharifinia et al.

    Microplastic pollution as a grand challenge in marine research: a closer look at their adverse impacts on the immune and reproductive systems

    Ecotoxicol. Environ. Saf.

    (2020)
  • W. Song et al.

    Midgut-derived activin regulates glucagon-like action in the fat body and glycemic control

    Cell Metabol.

    (2017)
  • J. Tower

    Mitochondrial maintenance failure in aging and role of sexual dimorphism

    Arch. Biochem. Biophys.

    (2015)
  • J. Wang et al.

    Polystyrene microplastics cause tissue damages, sex-specific reproductive disruption and transgenerational effects in marine medaka (Oryzias melastigma)

    Environ. Pollut.

    (2019)
  • S.L. Wright et al.

    Microplastic ingestion decreases energy reserves in marine worms

    Curr. Biol.

    (2013)
  • X. Xiong et al.

    Sources and distribution of microplastics in China's largest inland lake–Qinghai Lake

    Environ. Pollut.

    (2018)
  • L. Yin et al.

    Polystyrene microplastics alter the behavior, energy reserve and nutritional composition of marine jacopever (Sebastes schlegelii)

    J. Hazard Mater.

    (2018)
  • L. Yin et al.

    Polystyrene microplastics alter the behavior, energy reserve and nutritional composition of marine jacopever (Sebastes schlegelii)

    J. Hazard Mater.

    (2018)
  • L. Yin et al.

    Impacts of polystyrene microplastics on the behavior and metabolism in a marine demersal teleost, black rockfish (Sebastes schlegelii)

    J. Hazard Mater.

    (2019)
  • H. Zhang et al.

    Enhanced adsorption of oxytetracycline to weathered microplastic polystyrene: kinetics, isotherms and influencing factors

    Environ. Pollut.

    (2018)
  • Y. Zhang et al.

    Exposure to microplastics cause gut damage, locomotor dysfunction, epigenetic silencing, and aggravate cadmium (Cd) toxicity in Drosophila

    Sci. Total Environ.

    (2020)
  • Cited by (24)

    View all citing articles on Scopus
    View full text