Abstract

The increased global use of pyrethroids raises concern for non-target aquatic species. Bifenthrin, among the most predominantly detected pyrethroids in the environment, is frequently measured in water samples above concentrations reported to induce neuroendocrine and neurotoxic effects to several threatened and endangered fish species, such as the Chinook salmon and steelhead trout. To better characterize the neurotoxic effect of bifenthrin to salmonids, rainbow trout were treated with environmentally relevant concentrations of bifenthrin (15 and 30 ng/L) for two weeks and assessed for changes in transcriptomic profiles and histopathological alterations. The top bioinformatic pathways predicted to be impaired in bifenthrin-exposed trout were involved in gonadotropin releasing hormone signaling, the dysregulation of iron homeostasis, reduced extracellular matrix stability and adhesion, and cell death. Subsequent histopathological analysis showed a significant increase in TUNEL positive cells in the cerebellum and optic tectum of bifenthrin-treated trout, relative to controls (p < 0.05). These findings suggest that low, ng/L concentrations of bifenthrin are capable of dysregulating proper neuroendocrine function, impair the structural integrity of the extracellular matrix and cell signaling pathways in the brain, and induce apoptosis in neurons of juvenile salmonids following bifenthrin treatment, which is consistent with metabolomic profiles demonstrating a common target and mechanism.

Highlights

  • The widespread application of pyrethroid insecticides for agricultural and urban use within the last 20 years, largely in response to the phase-out of organochlorine and organophosphate insecticides [1], has raised concern for non-target aquatic species

  • Transcriptomic profiles were determined in the brains of rainbow trout, a surrogate to the critically endangered steelhead trout in California, following a two-week bifenthrin treatment to concentrations frequently measured within water samples (≤30 ng/L) from the Sacramento-San Joaquin Delta

  • Altered differentially expressed genes (DEGs) were incorporated into multiple functional annotation tools (GO, Kyoto Encyclopedia of Genes and Genomes (KEGG), and Ingenuity Pathway Analysis (IPA)), with genes involved in the top predicted pathways further validated using Quantitative Polymerase Chain Reaction (qPCR)

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Summary

Introduction

The widespread application of pyrethroid insecticides for agricultural and urban use within the last 20 years, largely in response to the phase-out of organochlorine and organophosphate insecticides [1], has raised concern for non-target aquatic species. This shift has increased the amount of pyrethroid active compounds applied worldwide, exceeding 8000 tons in 2014 [2]. Pyrethroids are comprised of Type I and Type II chemical classes. Type I pyrethroids include permethrin, allethrin, resmethrin, and bifenthrin and lack an α-cyano group, whereas type II classes include cypermethrin, deltamethrin, esfenvalerate, and lambda-cyhalothrin and carry an α-cyano moiety

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