<?xml version='1.0' encoding='utf-8'?>
<oai_dc:dc xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
  <dc:contributor>Karilyn E Sant</dc:contributor>
  <dc:contributor>Olivia L Venezia</dc:contributor>
  <dc:contributor>Alix B Shipman</dc:contributor>
  <dc:contributor>Stephen D. McCormick</dc:contributor>
  <dc:contributor>Alicia R Timme-Laragy</dc:contributor>
  <dc:creator>Monika A Roy</dc:creator>
  <dc:date>2019</dc:date>
  <dc:description>Background: 3,3’-Dichlorobiphenyl (PCB-11) is a non-legacy PCB congener widely detected in environmental samples and has been detected in human serum, but its toxicity potential is poorly understood.
Objectives: We measured PCB-11 in wild caught fish and assessed its embryotoxicity and interactions with the aryl hydrocarbon receptor (Ahr) pathway in developing zebrafish (Danio rerio). 
Methods: PCB-11 was measured in wild freshwater fish from a river in Western Massachusetts. In the laboratory, zebrafish embryos were exposed to 45 µg/L, 450 µg/L, or 4,500 µg/L PCB-11 from 24-96 hours post fertilization (hpf), when they were assessed for gross morphology and Cyp1a activity using the in vivo EROD bioassay. Ahr pathway interactions were probed by co-exposing zebrafish to the Ahr agonists PCB-126 and the model PAH beta-naphthoflavone (BNF). Liver development was assessed using the Tg(gut:GFP) zebrafish line. Zebrafish exposed to 4,500 µg/L PCB-11 were also collected at 96 hpf for qRT-PCR, RNAseq, and histology.
Results: Environmental concentrations of PCB-11 ranged from 103.0-136.0 ng/kg wet weight in wild fish tissue. Exposure to PCB-11 alone mildly affected EROD activity but did not affect gross morphology. However, 4,500 µg/L PCB-11 alone altered the expression of xenobiotic metabolism and liver development genes, impeded liver development, and increased vacuole formation in histology sections. In co-exposures, 4,500 µg/L PCB-11 prevented deformities caused by PCB-126 but exacerbated deformities in co-exposures with BNF. 
Discussion: PCB-11 is present in wild fish caught near a paper recycling facility in Western Massachusetts. Higher concentrations that may be present elsewhere such as the 4,500 µg/L PCB-11 concentration tested in zebrafish, can affect liver development, act as both a partial agonist/antagonist of the Ahr pathway, and act as an antagonist of Cyp1a activity to modify the toxicity of compounds that interact with the Ahr pathway.</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/j.envpol.2019.113027</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>The emerging contaminant 3,3’-dichlorobiphenyl (PCB-11) impedes Ahr activation and Cyp1a activity to modify embryotoxicity of Ahr ligands in the zebrafish embryo model (Danio rerio)</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>