Toxicological effects of pyraclostrobin on the antioxidant defense system and DNA damage in earthworms (Eisenia fetida)

2019 ◽  
Vol 101 ◽  
pp. 111-116 ◽  
Author(s):  
Junchao Ma ◽  
Chao Cheng ◽  
Zhongkun Du ◽  
Bing Li ◽  
Jinhua Wang ◽  
...  
RSC Advances ◽  
2021 ◽  
Vol 11 (43) ◽  
pp. 26481-26492
Author(s):  
Zhifeng Wang ◽  
Chaona Li ◽  
Yuanyuan Shao ◽  
Weina Xue ◽  
Ning Wang ◽  
...  

The integrated biomarker response (IBR) index was calculated to evaluate the integrated toxicological effects of PFOA on earthworm Eisenia fetida.


2012 ◽  
Vol 23 (4) ◽  
pp. 350-354 ◽  
Author(s):  
Aymelek Gönenç ◽  
Aysun Hacışevki ◽  
Sabahattin Aslan ◽  
Meral Torun ◽  
Bolkan Şimşek

2015 ◽  
Vol 87 ◽  
pp. S70
Author(s):  
Uraiwan Panich ◽  
Lapatsanant Chaisiriwong Chaisiriwong ◽  
Rungsima Wanitphakdeedecha ◽  
Panitta Sitthinamsuwan ◽  
Somruedee Chatsiricharoenkul ◽  
...  

2016 ◽  
Vol 124 ◽  
pp. 277-284 ◽  
Author(s):  
Imran Ali ◽  
Bohan Liu ◽  
Muhammad Ahsan Farooq ◽  
Faisal Islam ◽  
Azizullah Azizullah ◽  
...  

2021 ◽  
Author(s):  
Falin He ◽  
Hanmei Yu ◽  
Huijian Shi ◽  
Xiangxiang Li ◽  
Shanshan Chu ◽  
...  

Abstract 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 contaminants 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 confirm 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 damaged 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 t eco-toxicity potential of exogenous environmental pollutants in a real soil environment.


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