4.7 Article

Behavioral, histopathological, genetic, and organism-wide responses to phenanthrene-induced oxidative stress in Eisenia fetida earthworms in natural soil microcosms

Journal

ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH
Volume 29, Issue 26, Pages 40012-40028

Publisher

SPRINGER HEIDELBERG
DOI: 10.1007/s11356-022-18990-w

Keywords

Antioxidant defense response; Histopathological changes; DNA damage; Growth Inhibition; Toxic effects; Integrated biomarker response

Funding

  1. NSFC [U1806216, 21777088, 21477067]
  2. Cultivation Fund of the Key Scientific and Technical Innovation Project
  3. Research Fund for the Doctoral Program of Higher Education
  4. Ministry of Education of China [708058, 20130131110016]
  5. Science and Technology Development Plan of Shandong Province [2014GSF117027]

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This study evaluated the toxicity of phenanthrene (PHE) on earthworms and found that it induced oxidative stress, disrupted the antioxidant defense system, and caused damage in earthworms. Additionally, PHE resulted in behavior changes, histological damage, and inhibited growth and reproduction in earthworms. The study highlights the importance of investigating the eco-toxicity potential of exogenous environmental pollutants in a real soil environment.
Phenanthrene (PHE) contamination not only changes the quality of soil environment but also threatens to the soil organisms. There is lack of focus on the eco-toxicity potential of this contaminant in real soil in the current investigation. Here, we assessed the toxic effects of PHE on earthworms (Eisenia fetida) in natural soil matrix. PHE exhibited a relatively high toxicity to E. fetida in natural soil, with the LC50 determined to be 56.68 mg kg(-1) after a 14-day exposure. Excessive ROS induced by PHE, leading to oxidative damage to biomacromolecules in E. fetida, including lipid peroxidation, protein carbonylation, and DNA damage. The antioxidant defense system (total antioxidant capacity, glutathione S-transferase, peroxidase, catalase, carboxylesterase, and superoxide dismutase) in E. fetida responded quickly to scavenge excess ROS and free radicals. Exposure to PHE resulted in earthworm avoidance responses (2.5 mg kg(-1)) and habitat function loss (10 mg kg(-1)). Histological observations indicated that the intestine, body wall, and seminal vesicle in E. fetida were severely damaged after exposure to high-dose PHE. Moreover, earthworm growth (weight change) and reproduction (cocoon production and the number of juvenile) were also inhibited after exposure to this pollutant. Furthermore, the integrated toxicity of PHE toward E. fetida at different doses and exposure times was assessed by the integrated biomarker response (IBR), which confirmed that PHE is more toxic to earthworms in the high-dose and long-term exposure groups. Our results showed that PHE exposure induced oxidative stress, disturbed antioxidant defense system, and caused oxidative damage in E. fetida. These effects can trigger behavior changes and damage histological structure, finally cause growth inhibition, genotoxicity, and reproductive toxicity in earthworms. The strength of this study is the comprehensive toxicity evaluation of PHE to earthworms and highlights the need to investigate the eco-toxicity potential of exogenous environmental pollutants in a real soil environment.

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