Evidence map›Paper›PMID 25553538›Full record

ArticleAquatic toxicology (Amsterdam, Netherlands)2015

Regulation of pregnane-X-receptor, CYP3A and P-glycoprotein genes in the PCB-resistant killifish (Fundulus heteroclitus) population from New Bedford Harbor.

Johanna Gräns, Britt Wassmur, María Fernández-Santoscoy, Juliano Zanette, Bruce R Woodin, Sibel I Karchner, Diane E Nacci, Denise Champlin, Saro Jayaraman, Mark E Hahn and 2 more

Open access · greenAbstract read
In one paragraph

Article in Aquatic toxicology (Amsterdam, Netherlands), 2015. The graph could read no effect estimate from its abstract, so it casts no vote on the map. Cited by 14 papers.

0numbers the graph read from it
0cells of the map it votes in
14citing papers in PubMed
2.6field-weighted citation impact, top 13% of its field
1 · What the graph read from it

What it found

Each row is one number read from the abstract, on the scale the paper reported it, with its interval. Left of the dashed line favours the treatment, right favours the comparator. Under each row is the sentence it came from. New to these charts? A ten-minute tutorial.

The abstract states no effect estimate the extractor could read, or names no intervention and outcome on the map, so this paper lights no cell and moves no belief. It is still indexed, cited and linked below.

2 · The registry

The trial behind it

Trials whose registry record cites this paper, or whose number appears in the abstract. A trial that started after this paper was published is citing it as background, not reporting it.

Neither the registry nor the abstract names a trial number. If this is a trial report, that itself is worth knowing.

3 · Its place in the literature

Who cites it

14 citing papers in PubMed, 37 citations in OpenAlex.

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  13. Evolutionary toxicology in an omics world.Evolutionary applications · 2017
    Article
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4 · The record

Corrections and comments

PubMed lists nothing against this paper. Absence here is not a guarantee, only a check that was made.

5 · Who and what money

Authors and funding

12 authors at 3 institutions in 2 countries.

Johanna GränsDepartment of Biological and Environmental Sciences, University of Gothenburg, Box 463, SE 405 30 Gothenburg, Sweden.
Britt WassmurDepartment of Biological and Environmental Sciences, University of Gothenburg, Box 463, SE 405 30 Gothenburg, Sweden.
María Fernández-SantoscoyDepartment of Biological and Environmental Sciences, University of Gothenburg, Box 463, SE 405 30 Gothenburg, Sweden.
Juliano ZanetteBiology Department, MS #32, Woods Hole Oceanographic Institution, Woods Hole, MA 02543, USA.
Bruce R WoodinBiology Department, MS #32, Woods Hole Oceanographic Institution, Woods Hole, MA 02543, USA.
Sibel I KarchnerBiology Department, MS #32, Woods Hole Oceanographic Institution, Woods Hole, MA 02543, USA.
Diane E NacciOffice of Research and Development, National Health and Environmental Effects Research Laboratory, Atlantic Ecology Division, United States Environmental Protection Agency, 27 Tarzwell Drive, Narragansett, RI 02882, USA.
Denise ChamplinOffice of Research and Development, National Health and Environmental Effects Research Laboratory, Atlantic Ecology Division, United States Environmental Protection Agency, 27 Tarzwell Drive, Narragansett, RI 02882, USA.
Saro JayaramanOffice of Research and Development, National Health and Environmental Effects Research Laboratory, Atlantic Ecology Division, United States Environmental Protection Agency, 27 Tarzwell Drive, Narragansett, RI 02882, USA.
Mark E HahnBiology Department, MS #32, Woods Hole Oceanographic Institution, Woods Hole, MA 02543, USA.
John J StegemanBiology Department, MS #32, Woods Hole Oceanographic Institution, Woods Hole, MA 02543, USA.
Malin C CelanderDepartment of Biological and Environmental Sciences, University of Gothenburg, Box 463, SE 405 30 Gothenburg, Sweden. Electronic address: malin.celander@gu.se.
Woods Hole Oceanographic Institution · USUniversity of Gothenburg · SEEnvironmental Protection Agency · US

Funding

Training CoreP42ES007381 · NIEHS · BOSTON UNIVERSITY MEDICAL CAMPUS · PI SHERR, DAVID H · 1995 to 2019
$46.1M
NIEHS NIH HHS P42 ES007381NIEHS NIH HHS P42ES007381
6 · The paper itself

Abstract

Killifish survive and reproduce in the New Bedford Harbor (NBH) in Massachusetts (MA), USA, a site severely contaminated with polychlorinated biphenyls (PCBs) for decades. Levels of 22 different PCB congeners were analyzed in liver from killifish collected in 2008. Concentrations of dioxin-like PCBs in liver of NBH killifish were ∼400 times higher, and the levels of non-dioxin-like PCBs ∼3000 times higher than in killifish from a reference site, Scorton Creek (SC), MA. The NBH killifish are known to be resistant to the toxicity of dioxin-like compounds and to have a reduced aryl hydrocarbon receptor (AhR) signaling response. Little is known about the responses of these fish to non-dioxin-like PCBs, which are at extraordinarily high levels in NBH fish. In mammals, some non-dioxin-like PCB congeners act through nuclear receptor 1I2, the pregnane-X-receptor (PXR). To explore this pathway in killifish, a PXR cDNA was sequenced and its molecular phylogenetic relationship to other vertebrate PXRs was determined. Killifish were also collected in 2009 from NBH and SC, and after four months in the laboratory they were injected with a single dose of either the dioxin-like PCB 126 (an AhR agonist) or the non-dioxin-like PCB 153 (a mammalian PXR agonist). Gills and liver were sampled three days after injection and transcript levels of genes encoding PXR, cytochrome P450 3A (CYP3A), P-glycoprotein (Pgp), AhR2 and cytochrome P450 1A (CYP1A) were measured by quantitative PCR. As expected, there was little effect of PCB exposure on mRNA expression of AhR2 or CYP1A in liver and gills of NBH fish. In NBH fish, but not in SC fish, there was increased mRNA expression of hepatic PXR, CYP3A and Pgp upon exposure to either of the two PCB congeners. However, basal PXR and Pgp mRNA levels in liver of NBH fish were significantly lower than in SC fish. A different pattern was seen in gills, where there were no differences in basal mRNA expression of these genes between the two populations. In SC fish, but not in NBH fish, there was increased mRNA expression of branchial PXR and CYP3A upon exposure to PCB126 and of CYP3A upon exposure to PCB153. The results suggest a difference between the two populations in non-AhR transcription factor signaling in liver and gills, and that this could involve killifish PXR. It also implies possible cross-regulatory interactions between that factor (presumably PXR) and AhR2 in liver of these fish.

Indexed as

AnimalsATP Binding Cassette Transporter, Subfamily BCytochrome P-450 CYP3ADNA, ComplementaryFundulidaeGillsLiverMassachusettsPhylogenyPolychlorinated BiphenylsPregnane X ReceptorReceptors, SteroidWater Pollutants, ChemicalATP Binding Cassette Transporter, Subfamily BCytochrome P-450 CYP3ADNA, ComplementaryPolychlorinated BiphenylsPregnane X ReceptorReceptors, SteroidWater Pollutants, ChemicalCYP3AFishNR1I2PCBP-glycoproteinPXR

Identifiers

PMID25553538
PMCPMC4311260
OpenAlexW1979191700

What OpenQuestion holds

Textmetadata
LicenceTDM
Read underepoch 390

Registered trials

None linked

Read under generation 80e0d062 · epoch 390. Bibliography from PubMed, PubMed Central and OpenAlex; grants from NIH RePORTER; trial links from ClinicalTrials.gov; estimates, votes and beliefs from the OpenQuestion graph.