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

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 ( E...

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Veröffentlicht in:Environmental science and pollution research international 2022-06, Vol.29 (26), p.40012-40028
Hauptverfasser: He, Falin, Yu, Hanmei, Shi, Huijian, Li, Xiangxiang, Chu, Shanshan, Huo, Chengqian, Liu, Rutao
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container_issue 26
container_start_page 40012
container_title Environmental science and pollution research international
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creator He, Falin
Yu, Hanmei
Shi, Huijian
Li, Xiangxiang
Chu, Shanshan
Huo, Chengqian
Liu, Rutao
description 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 LC 50 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.
doi_str_mv 10.1007/s11356-022-18990-w
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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 LC 50 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. 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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 LC 50 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 ). 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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. 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source MEDLINE; Springer Nature - Complete Springer Journals
subjects Animals
Antioxidants
Antioxidants - metabolism
Aquatic Pollution
Atmospheric Protection/Air Quality Control/Air Pollution
Biomarkers
Body wall
Carbonyls
Carboxylesterase
Catalase
Catalase - metabolism
Contaminants
Contamination
Damage
DNA damage
Earth and Environmental Science
Ecotoxicology
Eisenia fetida
Environment
Environmental Chemistry
Environmental Health
Environmental science
Exposure
Free radicals
Genotoxicity
Glutathione
Glutathione transferase
Intestine
Lipid peroxidation
Lipids
Malondialdehyde - metabolism
Microcosms
Oligochaeta
Oxidative Stress
Peroxidase
Peroxidation
Phenanthrene
Phenanthrenes - metabolism
Pollutants
Reactive Oxygen Species - metabolism
Research Article
Seminal vesicle
Soil - chemistry
Soil contamination
Soil environment
Soil Pollutants - metabolism
Soil pollution
Soil quality
Soils
Superoxide dismutase
Superoxide Dismutase - metabolism
Toxicity
Waste Water Technology
Water Management
Water Pollution Control
Worms
title Behavioral, histopathological, genetic, and organism-wide responses to phenanthrene-induced oxidative stress in Eisenia fetida earthworms in natural soil microcosms
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