Organisms chronically exposed to organic pollutants such as polychlorinated biphenyls (PCBs) can develop resistance to these chemicals, a condition associated with reduced inducibility of the biomarker enzyme cytochrome P450 1A (CYP1A). This study addresses the CYP1A response of members of the families Ictaluridae and Centrarchidae, two fish families found throughout much of the United States. We measured CYP1A expression, PCB body burdens, and conducted CYP1A challenge experiments in species from these families residing in the Town Branch/Mud River system (Logan County, KY, USA), a stream system historically contaminated with high levels of PCBs. Despite PCB concentrations in muscle tissue typically associated with elevated CYP1A (16.7 to 75.2μgPCB/g wet edible flesh), resident fish in the contaminated Town Branch/Mud River sites (yellow bullhead [Ameiurus natalis], green sunfish [Lepomis cyanellus], and spotted bass [Micropterus punctulatus]) had hepatic CYP1A activity levels similar to, rather than higher than, those in reference fish, suggesting reduced sensitivity to CYP1A induction. Lack of CYP1A expression following direct contaminant exposure has often been associated with resistance to those contaminants. To determine if CYP1A in resident populations was resistant to induction by PCBs, we exposed resident fish to a single, intraperitoneal injection with a potent CYP1A inducer, 3,4,3',4'-tetrachlorobiphenyl (PCB 77). PCB 77 treatment significantly induced hepatic CYP1A activity and protein in yellow bullhead from reference, but not contaminated, sites and had no effect on CYP1A in green sunfish from either site. The low CYP1A expression levels in resident fish with elevated PCB body burdens, together with the failure of PCB injection to induce CYP1A in certain populations, indicate an acclimatory CYP1A response in yellow bullheads and likely an inherently resistant CYP1A in green sunfish. This work demonstrates for the first time acclimation of CYP1A to PCBs in a species within the family Ictaluridae and provides further support for our previous work indicating an apparent inherent lack of CYP1A sensitivity to chlorinated inducers in Centrarchids. These traits may explain, at least in part, the common association of these families with degraded habitats and indicate Lepomis members are likely to be excellent candidates for exploring the mechanistic basis of 'inherent' CYP1A resistance. This study also underlines to the need for thorough characterization of the CYP1A responsivity of a population and/or species prior to using CYP1A as a reliable biomonitoring tool.
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http://dx.doi.org/10.1016/j.cbpc.2012.07.001 | DOI Listing |
J Hazard Mater
December 2024
College of Environmental Science and Engineering, North China Electric Power University, Beijing 102206, China. Electronic address:
This study aimed to investigate the differences in the mechanisms of microscopic hepatotoxicity, developmental toxicity, and neurotoxicity in aquatic organisms co-exposed to styrene-butadiene rubber tire microplastics (SBR TMPs) and fluoroquinolone antibiotics (FQs). We found that hepatotoxicity in zebrafish induced by SBR TMPs and FQs was significantly higher than developmental toxicity and neurotoxicity. Furthermore, the main effects of the FQs primarily manifested as synergistic toxicity, whereas the low- and high-order interactions of the FQs mainly exhibited synergistic and antagonistic effects, respectively.
View Article and Find Full Text PDFSci Total Environ
December 2024
Department of Paraclinical Sciences, Norwegian University of Life Sciences, Oslo, Norway.
The overall aim of the present study was to determine if exposure to three high volume plastic additives, including diethylhexyl phthalate (DEHP), bisphenol A (BPA) and benzotriazoles (BT), have the potential to promote adverse effects in Atlantic cod (G. morhua). Ex vivo precision cut - liver slices (PCLS) from six male juvenile Atlantic cod were exposed to four concentrations of mono-(2-ethylhexyl)-phthalate (MEHP, the main metabolite of DEHP), BPA and BT both singly and in mixtures ranging from 0.
View Article and Find Full Text PDFChemosphere
December 2024
Department of Environmental and Molecular Toxicology and the Oregon State University Superfund Center, Oregon State University, ALS 1007, Corvallis, OR, 97331, USA. Electronic address:
Polycyclic aromatic hydrocarbons (PAHs) are a diverse class of chemicals that occur in complex mixtures including parent and substituted PAHs. To understand the hazard posed by complex environmental PAH mixtures, we must first understand the structural drivers of activity and mode of action of individual PAHs. Understanding the toxicity of alkylated PAHs is important as they often occur in higher abundance in environmental matrices and can be more biologically active than their parent compounds.
View Article and Find Full Text PDFEcotoxicol Environ Saf
December 2024
Department of Biological and Environmental Sciences, University of Gothenburg, Gothenburg 405 30, Sweden. Electronic address:
In vitro models based on permanent fish liver cell lines have proven to be versatile tools for examining chemical biotransformation and toxicity. However, their in vivo relevance remains uncertain due to their potentially de-differentiated phenotype. Here, we investigate whether a 3D cell culture environment can restore hepatocyte-like properties of the Rainbow trout liver cell line RTL-W1.
View Article and Find Full Text PDFMar Pollut Bull
December 2024
Department of Physical, Earth and Environmental Sciences, University of Siena, Via Mattioli 4, 53100 Siena, Italy. Electronic address:
The present study investigates the potential interaction between nano‑titanium dioxide (nano-TiO) and the water accommodated fraction (WAF) of crude oil and associated chemicals on bioavailability and biotransformation responses in the European sea bass (Dicentrarchus labrax). An in vivo (48-h) waterborne exposure with nano-TiO (10 mgL), crude oil WAF (0.068 gL), alone and in combination was performed.
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