Sensitivity to environmental stressors largely depend on the genetic complement of the organism. Recent sequencing and assembly of teleost fish genomes enable us to trace the evolution of defense genes in the largest and most diverse group of vertebrates. Through genomic searches and in-depth analysis of gene loci in 76 teleost genomes, we show here that the xenosensor pregnane X receptor (Pxr, Nr1i2) is absent in more than half of these species. Notably, out of the 27 genome assemblies that belong to the Gadiformes order, the pxr gene was only retained in the Merluccidae family (hakes) and Pelagic cod (Melanonus zugmayeri). As an important receptor for a wide range of drugs and environmental pollutants, vertebrate PXR regulate the transcription of a number of genes involved in the biotransformation of xenobiotics, including cytochrome P450 enzymes (CYP). In the absence of Pxr, we suggest that the aryl hydrocarbon receptor (Ahr) have evolved an extended regulatory role by governing the expression of certain Pxr target genes, such as cyp3a, in Atlantic cod (Gadus morhua). However, as several independent losses of pxr have occurred during teleost evolution, other lineages and species may have adapted alternative compensating mechanisms for controlling crucial cellular defense mechanisms.
Teleost fishes represent the largest and most diverse vertebrate clade. By inhabiting a wide range of oceanic and freshwater habitats, ranging from tropical to arctic regions, the genetic composition and phenotype of teleost fishes have evolved accordingly1,2. However, genes involved in the orchestrated cellular recognition, biotransformation and elimination of chemical compounds, denoted the chemical defensome, are largely conserved through evolution3,4,5. Today, the increasing burden of man-made compounds poses a great risk to the aquatic environment. Since large pelagic and benthic teleost fish are the dominant group of predators in global oceans, they are particularly vulnerable to ecosystem-wide changes in energy resources6, such as those caused by pollution. Thus, understanding the genomic defense mechanisms and their downstream effects in these species is paramount in conserving environmental diversity.
Atlantic cod (Gadus morhua) was the first commercially important, large teleost species of which the genome was sequenced and assembled7. Furthermore, it is commonly used as an indicator species in environmental monitoring programs and is an emerging marine model organism in toxicological studies8,9,10,11. Due to its habitats near offshore oil platforms, petroleum recovery facilities and coastal industries, the effects of contaminants in Atlantic cod are of great interest12,13,14,15. We have recently mapped the full suite of cod cytochrome p450 (cyp) genes, providing further clues to the inherent capabilities for biotransformation of endogenous and xenobiotic compounds in this species16. However, the proteins that regulate various chemical defense mechanisms have not been described in Atlantic cod.
Pregnane X receptor (PXR, NR1I2) and constitutive androstane receptor (CAR, NR1I3) are considered two of the main xenobiotic receptors in mammals that, in addition to binding endogenous steroid hormones, are activated by a structurally diverse range of drugs and environmental pollutants. Primarily expressed in the liver and small intestine, these xenosensors regulate the transcription of biotransformation enzymes, such as cytochrome P450 3A (CYP3A), and are thus central in orchestrating the chemical defensome. PXR and CAR belong to the large family of ligand-activated transcription factors known as nuclear receptors (NR), more specifically the subfamily NR1I, and show the common NR structural organization of a highly conserved DNA-binding domain (DBD) and a less conserved ligand-binding domain (LBD)17. The early evolutionary history of this subfamily is not clear, but the NR1I genes are hypothesized to diverge from a common ancestral gene, such as that identified in the chordate invertebrate Ciona intestinalis18. A vitamin D receptor (VDR, NR1I1) has been cloned from sea lamprey (Petromyzon marinus), an ancient vertebrate lacking calcified skeleton and jaws, and proposed to function in part as a xenosensor19. However, early in, or before, vertebrate evolution, this ancestral gene diverged into VDR and PXR18.
Phylogenetic analyses suggest that the further divergence of CAR and PXR occurred in a whole genome duplication (WGD) in, or prior to, the formation of the vertebrate crown lineage, Sarcopterygii20. However, except for mammals, which have retained both xenosensors, several independent losses of CAR and PXR have occurred in vertebrate evolution, leaving birds and lizards with CAR (also known as CXR21) and teleost species with PXR22,23,24. The aryl hydrocarbon receptor (Ahr) is another important transcription factor in the chemical defensome of vertebrates. Also known as the “dioxin receptor”, the ligands of this basic-Helix-Loop-Helix-PAS domain receptor include environmental pollutants such as 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and certain planar polycyclic aromatic hydrocarbons like benzo[a]pyrene. The most studied piscine Ahr target gene is cyp1a12,25, but recent studies have indicated its co-regulative role in mediating transcription of the Pxr target gene, cyp3a65, in zebrafish26,27,28.
The aim of the present study was to examine the evolution of Pxr orthologs in teleost fish. Importantly, based on global genomic searches and in-depth analysis of gene loci of 76 teleost genome assemblies29,30, we show that several independent losses of pxr have occurred during piscine evolution. Furthermore, although we show that a pxr gene is absent in most species in the Gadiformes order, we detect its presence in the Merluccidae (hakes) family. Moreover, by mapping the complete NR complement in Atlantic cod, we show that the other nuclear receptors are conserved in this Gadiform species. Finally, lack of Pxr agonist-induced transcriptional response in Atlantic cod liver, as well as a highly increased number of putative Ahr response elements in the promoter region of Pxr target genes, suggest that Ahr has evolved a compensatory role in the absence of Pxr in this species. However, as several independent losses must have occurred during teleost evolution, other lineages may have adapted other compensating mechanisms. This is the first report with compelling evidence for multiple independent losses of the pxr gene in vertebrate evolution and accentuate the need for understanding how the chemical defensome system has evolved in teleost fish.
In silico searches in 76 sequenced and assembled teleost genomes and using zebrafish Pxr as query sequence, showed that a pxr gene could not be identified in the majority of the fish species (Fig. 1). Additional searches using Pxr from medaka or tetraodon gave similar results (Supplementary Fig. 1). Surprisingly, pxr was only present in 33 out of the 76 genomes analyzed. Searches performed using zebrafish Vdrα as query, however, showed that a vdr gene was present in all species (Supplementary Fig. 2).
As a positive control of the pipeline used for the gene mapping, searches using zebrafish Mhc II were included, showing an identical phylogenetic distribution as published previously (Fig. 1)29. Multiple hits on the NR DBD are the result of the high similarity between these domains in the different NR proteins within a genome.
Furthermore, we analyzed the genomic scaffolds containing MAATS1 and GSK3B, which flank PXR in all examined phyla that possess PXR. Figure 2 shows that the syntenic relationship of these genes is also maintained throughout the evolution of fishes. Importantly, in Atlantic cod and other species where pxr was not identified, no gene is present in the genomic region between maats1 and gsk3b. Our results show that the loss of pxr has occurred in several orders, including Zeiformes, Holocentriformes, and Beryciformes. Importantly, out of the 27 genome assemblies in the Gadiform order, we only identified sequences similar to Pxr in the Merluccidae family (hakes, represented by M. polli, M. merluccius, and M. capensis) and Melanonus zugmayeri (Pelagic cod). The syntenic relationship of maats1 and pxr was confirmed in European hake (M. merluccius), while gsk3b was assembled to another scaffold (Fig. 2).
In order to explore whether the presence of Merluccidae and Melanonidae pxr was due to retention or introgression, we aligned the translated LBDs of the identified Pxr sequences. Since Vdr (Nr1i1) are in the same NR subfamily as Pxr, we also included known teleost orthologs of this receptor, as well as orthologous retinoic acid receptor (Rarγ, Nr1b3) and Rev-Era (Nr1d1) sequences as an outgroup. Although the families are distantly related, the sequences identified from Melanonus and Merluccius genomes are grouped together in the resulting phylogenetic tree, showing that their Pxr sequences are specific for the Gadiformes order (Fig. 3). The phylogeny also supported our initial bioinformatic searches, as none of the Pxr sequences grouped with the teleost Vdr sequences. However, some short sequences that were identified using medaka and tetraodon Pxr as query (Supplementary Fig. 1) were found to group with Rarγ and Rev-Erbα (Nr1d1), and not Pxr (Fig. 3). While loss of the third member of the NR1I subgroup in mammals, CAR, is demonstrated previously in teleost fish22,31, we also performed searches using the unusual Xenopus laevis BXR32 without identifying any new Pxr-similar sequences.
Thus, our investigations support the hypothesis that Pxr is retained in Merluccidae and Melanonidae even though several, possibly three, losses of pxr have occurred in the evolution of the Gadiformes order alone (Fig. 4).
In the Atlantic cod genome (gadMor17), HMM-searches identified 72 nuclear receptor-encoding genes, which were further mapped to 50 unique members of the NR superfamily (Supplementary Table 2). To visualize their phylogenetic relationship and distribution into the NR families and subfamilies, the NR complement of Atlantic cod and zebrafish were compared by multiple sequence alignments and visualized as a cladogram (Fig. 5). Importantly, whereas the zebrafish NR1I subfamily contains Pxr (Nr1i2) and two paralogous Vdr proteins (Nr1i1a and Nr1i1b, denoted Vdrα and Vdrβ), only Vdrα and Vdrβ orthologs were identified in the cod genome. Furthermore, the cod genome holds additional orthologs to defensome-related NRs that are not identified in the zebrafish genome, including retinoic acid receptors (i.e. two nr1b2 genes, and one nr1b3), hepatocyte nuclear factor 4a (nr2a1), glucocorticoid receptor (nr3c1), and androgen receptor (nr3c4).
Searches in the second version of the Atlantic cod genome assembly (gadMor233) supported the absence of a pxr gene. Moreover, we made several attempts to amplify a pxr transcript from cod liver cDNA through polymerase chain reactions (PCR) using CODEHOP primers (Supplementary Table 3). These primers have previously been used to amplify pxr in other fish species, including Atlantic herring (Clupea harengus), Atlantic wolfish (Anarhichas lupus) and European eel (Anguilla anguilla) (Supplementary Table 5). In line with the results from the bioinformatic searches, we were also able to successfully amplify pxr from the Gadiform species European hake (Merluccius merluccius) (Supplementary Table 5). In contrast, none of the primers amplified sequences that matched pxr orthologs when using Atlantic cod cDNA as template.
To study the transcriptional effect on the biotransformation genes cyp3a and cyp1a, we exposed precision-cut liver slices (PCLS) from Atlantic cod to a selected set of compounds known to activate mammalian and piscine PXR, and cod Ahr (BNF). The results show that the model zebrafish Pxr agonist, clotrimazole, had no significant effect on the transcription of cyp3a169 and cyp3a166, but it did induce transcription of cyp1a (p < 0.05) (Fig. 6a). Transcription of all genes were slightly, but significantly (p < 0.05) affected by the mouse PXR agonist, PCN, whereas the human PXR agonist, rifampicin, and the medaka Pxr agonist, B4HB, significantly (p < 0.05) affected transcription of both cyp3a169 and cyp1a (Fig. 6a). Although slightly more induced than the cyp3a genes, the induction of cyp1a was much less following exposure to these compounds, compared to the exposure with the Ahr agonist, BNF (Fig. 6b). The highest dose of BNF also affected the transcription of both cyp3a genes, but the mean fold change remained low. Finally, we mapped the XRE and putative NR response elements (REs) in a 13,000 base-pair region upstream of the transcription start sites of human, mouse, zebrafish, and Atlantic cod CYP3A and CYP1A orthologs. These results show that the three active PXR-specific REs determined for human CYP3A434 are not conserved between these species, including mouse (Supplementary Fig. 2). The clusters of known XREs in human CYP1A1, mouse Cyp1a1 and zebrafish cyp1a orthologs35,36,37, however, appear to be conserved and coincide position-wise. Importantly, whereas NR REs dominate the promoter regions of mammalian CYP3A genes, the promoter regions of the fish cyp3a orthologs have a higher number of potential XREs (Fig. 6c). Furthermore, the promoter regions of cod cyp3a166, cyp3a169, and cyp1a contain almost twice the number of putative XREs than zebrafish (Fig. 6c).
In the present work, we have demonstrated that multiple losses of pxr have occurred during teleost evolution. Through global genomic searches and in-depth analysis of gene loci of 76 teleost genome assemblies, we show that only 33 of these species have retained a pxr gene. Notably, our results show that within the Gadiformes order, only the Merluccidae family (hake) and Melanonus zugmaeri (Pelagic cod) have retained pxr, whereas the 23 other gadiform species represented have lost the gene. Based on current phylogeny of Malmstrøm, et al.29, Merluccidae and Melanonidae are on separate branches deep within the Gadiformes order, and have arisen later in evolution than Bregmaceros cantori (striped codlet) but earlier than Macrouridae (grenadiers) and Muraenolepis marmorata (marbled moray cod), which all have lost the pxr gene. Thus, the presence of pxr in Merlucciudae and Melanonidae could be due to retention of an ancestral gene together with several independent losses in the other Gadiform species, or it could have been reintroduced through introgression. As we demonstrate through the conserved syntenic relationship of the genomic region, and the phylogenetic pattern of the LBD of Merluccidae and Melanonus zugmayeri Pxrs, it is most likely that an ancestral gene is retained in these species. Moreover, based on current phylogeny, this means that multiple, independent losses have occurred in evolution of the Gadiformes order alone.
In other vertebrate species, PXR is an important xenobiotic receptor that governs much of the transcriptional response to chemical stressors. For instance, human PXR directly regulate expression of CYP3A isozymes, which are involved in the metabolism of more than 50% of all prescription medicines38. Cyp3a genes have been cloned and functionally characterized in several fish species39,40,41,42,43,44,45, but, with the exception of zebrafish28, the transcriptional regulation of teleost cyp3a genes remains largely unexplored. However, exposure to prototypical Pxr agonists resulted in upregulated transcription of cyp3a genes in Atlantic killifish (Fundulus heteroclitus), zebrafish liver and rainbow trout (Oncorhynchus mykiss)46,47,48. Furthermore, expression patterns of the subfamilies cyp3b, cyp3c, and cyp3d in ray-finned fishes (Actinopterygii) suggest involvement in xenobiotic metabolism, but this role has not yet been demonstrated11,49,50,51. Thus, the widespread absence of pxr orthologs in teleosts, and particularly among Gadiform species, raise interesting questions on how transcriptional regulation of biotransformation enzymes in these species has evolved.
By using Atlantic cod (Gadus morhua) as a representative of a teleost without pxr, we mapped the full complement of NR genes and show that Pxr is absent in the Nr1i subgroup. In line with the genome mining and syntheny analysis, we were unable to amplify a pxr gene from cod liver using CODEHOP primers. Notably, we were successful in using the primers to amplify a pxr ortholog from European hake (Merluccius merluccius), one of the few Gadiform species that have retained this gene.
Furthermore, we explored how transcription of cod cyp3a and cyp1a genes were affected by exposure to classical Pxr agonists. Exposure of cod PCLS to potent in vitro activators of human, mouse, zebrafish, and medaka PXR/Pxr, including rifampicin, PCN, clotrimazole, and p-hydroxybenzoic acid, respectively52, had little or no effect on cyp3a transcript levels. Furthermore, although exposure to the established cod Ahr agonist BNF had a significant effect on cyp3a transcription at the highest dose, the fold increase was very low compared to the BNF induction of cyp1a. Similarly, in an early study of Atlantic cod, hepatic distribution of a CYP3A-like isozyme P450b remained unaffected after in vivo exposure to BNF53. In mice, basal levels of Cyp3a11 expression was elevated approximately 4-fold in the livers of PXR knockouts relative to their wild-type counterparts54, suggesting that PXR also has a repressing transcriptional role. We recently found a significant decrease in cod cyp3a expression in PCLS following a 24-hour exposure to 10 μM ethynylestradiol55. This is in line with previous studies that indicate that xenoestrogens affect the expression and activity of Cyp3a and Cyp1a in Atlantic cod and Atlantic salmon (Salmo salar)8,56,57, and suggests that the estrogen receptor (Er) signaling pathway also is involved in controlling cyp3a expression in these species. Interestingly, the level of human ER proteins is partly regulated by activated AhR, which act as a ubiquitin ligase that selectively target sex steroid receptors for protein degradation58.
In order to further decipher the transcriptional regulation of Atlantic cod cyp3a and cyp1a orthologs in the absence of Pxr, we mapped the response elements in the 13 000 bp promoter region of these genes. The activated RXR/PXR heterodimer can bind several types of NR response elements, such as direct repeats (DR3, DR4, and DR5), inverted repeats (IR6), and everted repeats (ER6 and ER8)59,60,61,62. In humans, the active PXR response elements in the CYP3A4 promoter are known to include a distal enhancer module containing a DR3 motif, a xenobiotic-responsive enhancer module (XREM) containing a DR3 and an ER6 motif, and a proximal ER663,64. In addition, an HNF4α binding element (DR1/IR1) is important in transcriptional regulation of both human CYP3A4 and mouse Cyp3a1165,66. Although the active PXR response elements are to some extent conserved between primates34, we did not find these in mouse Cyp3a11 or fish cyp3a promoter regions. Notably, whereas the promotor regions of the mammalian CYP3A4 and Cyp3a11 were dominated by NR response elements, the promoter regions of the teleost orthologs also included Ahr-binding xenobiotic response elements (XRE). In fact, we found that the relative number of XREs in the promoter region of cod cyp3a orthologs are higher than in zebrafish cyp3a65, where it is demonstrated that Ahr are necessary to mediate effective transcription of this gene27. Although the active XREs needed for transcription of human CYP1A1, mouse Cyp1a1, and zebrafish cyp1a are well described35,37,67, we were not able to recognize the position of these sites in the cod ortholog. However, similar to the promoter regions of cod cyp3a166 and cyp3a169, we found that both the relative number of XREs, as well as the total number of response elements, in the cod cyp1a promoter region are higher than in the human, mouse, and zebrafish orthologs. Thus, transcriptional regulation of cod cyp3a genes appears more complex and may include extended coordinated signaling pathways and receptor crosstalk. This raises the question whether cod, and other fish lacking pxr, have a different response and sensitivity to environmental contaminants compared to fish that have retained the gene. When juvenile cod and rainbow trout (Oncorhynchus mykiss) were exposed in parallel to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) – a potent agonist for the aryl hydrocarbon receptor, cod liver accumulated higher concentrations compared to trout, whereas that hepatic Cyp1a1 activity was lower68. Furthermore, exposing cod and turbot (Scophthalamus maximus) to two xenoestrogens, 4-nonylphenol and bisphenol A, showed indication of cod being the most sensitive and less specific in its response69. The genomes of trout and turbot were not included in our study, but whereas pxr is previously identified in rainbow trout47, we have not been able to clone this gene from turbot (unpublished results). Thus, it seems that there are inherent differences in how these fish species respond to chemicals that primarily interact with other receptor pathways, but, to our knowledge, a similar comparison aiming to activate the Pxr-pathway has not yet been published.
In addition to its xenosensing role, PXR has frequently been linked to functions in the immune system of mammals, such as co-regulation of CYPs70,71,72,73 and cross-talk with the inflammation and immune responding transcription factor NF-κB74,75,76. Interestingly, the initial sequencing of the Atlantic cod genome revealed the absence of several genes important for the adaptive immune system in other vertebrates, including the genes encoding the major histocompatibility complex (Mhc) II, Cd4 and invariant chain (II)7,77. Furthermore, low coverage genome sequencing of 66 teleost species demonstrated the absence of mhcii across the entire Gadiformes order29. However, whereas all Gadiformes, but no other fish genomes studied so far, lack mhcii78, our study show that the loss of pxr is not specific for the Gadiform order but has occurred several times during teleost evolution.
In conclusion, we present the first comprehensive evidence for evolutionary loss of the Pxr in teleost fish. Importantly, the evolutionary pattern strongly suggests that multiple independent losses of this important xenobiotic receptor have occurred early in the Gadiformes order, as well as in several other teleost lineages. Furthermore, we suggest that the Ahr has evolved a regulatory role for cyp gene transcription in Atlantic cod. The loss of pxr, and possible evolved compensatory mechanisms for the lack of this gene, adds to the scientific interest in Atlantic cod as a toxicological model species. However, as several independent losses have occurred in the course of teleost evolution, other lineages may have adapted other compensating mechanisms, which accentuate the need for understanding how the chemical defensome has evolved in fish.
Material and Methods
Searching 76 teleost species for a pxr gene
The selection of teleost genomes was performed based on the most robust and recent multi-genome phylogeny available at the time of the study29,30. This list includes 66 low-coverage genome assemblies29,30, including 27 species from the Gadiformes order and a newly published cod genome assembly33, and 10 other published teleost genomes (listed in Supplementary Table 13). Performing tBLASTn searches, the nucleotide sequence of the fish genome assemblies was searched using the amino acid sequence of Pxr from zebrafish (protein id. A5WYG8), medaka (Oryzias latipes, H2MUK7), tetraodon (Tetraodon nigroviridis, H3D8U6), and BXRβ from Xenopus laevis (Q9DF24) as query. To remove false positive BLAST hits that corresponded to the vitamin D receptor (Vdr, Nr1i1), we removed any BLAST hits that also was listed as Vdr from the same fish species (i.e. zebrafish Vdrα: Q9PTN2, medaka Vdr: H2MP78, and tetraodon Vdrα: H3CJ29) at a lower e-value. The output file of each search defined the coordinates (amino acid number for start and end) of the identified nucleotide segments (blast hits) in relation to the query Pxr sequence used. Based on these coordinates, it was counted how many times every position in the query Pxr sequence was overlapped by the identified segments, providing a coverage vector. The resulting coverage vectors of the BLAST hits identified from the Pxr of each sequence were assembled and visualized as a heat map, guided by the phylogenetic tree published in Malmstrøm et al.29. In these heat maps, one cell represents one amino acid in the Pxr sequence (x-axis) identified in the 76 different fish species (y-axis).
As a positive control of this approach, we applied this pipeline to search for the mhcii gene in the 76 fish genome assemblies, whose phylogenetic distribution in teleosts is recently characterized29.
Based on their ligand binding domains, sequences identified in the bioinformatic searches using zebrafish, medaka, and tetraodon Pxr as query were aligned with annotated or cloned teleost Pxr (Nr1i1), Vdr (Nr1i2), retinoic acid receptor (RARγ, Nr1b3) and Rev-ERbα (Nr1d1), using Clustal Omega v1.2.2 with default parameters (https://doi.org/10.6084/m9.figshare.6204920). Due to incomplete sequences in the LBD, Cyttopsis roseus, Neoniphon samara, Lesueurigobius cf., and Holocentrus rupus was excluded from the alignment. The maximum likelihood phylogeny was analyzed in RAxML v 8.1.14 using the CATLG model, with 200 bootstrap replicates, and drawn in FigTree v.1.4.2. The figure was prepared in Adobe Illustrator CS5.
Syntenic relationship analysis
The genomic region containing the mammalian PXR gene is conserved, with MAATS1 located immediately downstream and GSK3B immediately upstream of PXR. We used BLAST and Exonerate (EMBL-EMI) to search for these genes in 76 teleost genome assemblies29. Since the searches were performed in relatively fragmented genome assemblies, synteny was only revealed in the assemblies where the genes were located on the same scaffold. The phylogenetic relationships between the different teleost species were derived from Malmstrøm et al.29.
Identifying nuclear receptors in the Atlantic cod genome
We identified the cod NR proteins in the Atlantic cod protein database (ENSEMBL-Gadus_morhua.gadMor.1.73, based on gadMor1 annotated proteins) by hidden Markov model (HMM) searches using HMMER v3.1b1 (www.hmmer.org) and the Pam profiles ‘Hormone_recep’ PF00104.25 and ‘zf-C4’ PF00105.1379. A Python script (available at https://doi.org/10.6084/m9.figshare.5752791) was used to perform the HMM searches, which were followed by reciprocal BLAST searches against the well-annotated zebrafish (Danio rerio) proteome (ENSEMBL-Danio_rerio.Zv9.73) to predict orthologous proteins. Based on the ENSEMBL protein identifiers, the corresponding gene identifiers were identified in the ENSEMBL databases and are presented in Supplementary Table 2.
Further, specific tblastn searches were also performed in the second version of the cod genome assembly (gadMor2; available at http://cees-genomes.hpc.uio.no/blast/33), using zebrafish Pxr (protein id. A5WYG8-1) as query sequence. The resulting gene entries were extracted and orthologs identified by reciprocal blastp searches in the UniProtKB database.
Phylogenetic analyses of the NR-superfamily
A multiple sequence alignment of the Atlantic cod and zebrafish nuclear receptor proteins (available at https://doi.org/10.6084/m9.figshare.5752812) was constructed using ClustalX 2.1. Based on the resulting alignment, a phylogenetic tree was constructed using MrBayes v3.2.3 with the following settings: the prior for the amino acid model was set to mixed, and the number of generations used was 100 00080. FigTree v1.3.1 was used to visualize the tree, and the figure was prepared in Adobe Illustrator. For genes with predicted multiple protein sequences (splice variants), only the longest translation was included to ensure a non-redundant sequence set.
Amplifying pxr from cod liver with consensus-degenerate hybrid oligonucleotide primers
Total RNA was extracted from liver tissue from two different cods using phenol and guanidinium isothiocyanate solution (Trizol, Thermo Fisher Scientific), before Superscript II Reverse transcriptase was used to synthesize cDNAs from total RNA as described by the supplier (Invitrogen). Consensus-degenerate hybrid oligonucleotide (CODEHOP) primers (Supplementary Table 3) were designed based on known Pxr sequences from eight fish species fish and human PXR (Supplementary Table 4) using the CODEHOP web tool81. The PCRs were performed using GoTaq DNA polymerase according to the protocol from the supplier (Promega) as gradient PCRs (Tanneal: 46–60 °C).
Ex vivo exposure to compounds known to activate mammalian and piscine PXR
Atlantic cod (Gadus morhua) was provided from Fjord Gadus AS (Fiskå, Norway), and maintained at The Industrial and Aquatic Research Laboratory (ILAB, Bergen, Norway). The fish were kept in 500 L tanks in natural seawater at 9 °C with a 12:12 hour light cycle regime. The fish were fed with a commercial diet ad libitum (EWOS, Bergen, Norway). Six immature cod of mixed sex, weighing 840–1549 g, was used in these experiments.
The fish were handled by FELASA C (Federation of European Laboratory Animal Science Association) approved personnel and killed according to the directions from the Norwegian Food Safety Authority (FOTS) § 16, second paragraph. Preparation of cod precision-cut liver slices (PCLS) was performed as described previously10. Freshly prepared cod PCLS were exposed for 24 hours to prototype PXR/Pxr-ligands described from other species, including clotrimazole, pregnenolone 16α-carbonitrile (PCN), rifampicin, and p-hydroxy benzoic acid (B4HB)52, as well as the well-known cod Ahr-ligand and cyp1a-inducer β-naphthoflavone (BNF). Chemicals were purchased from Sigma-Aldrich (Oslo, Norway) and dissolved in Hybri-Max™ dimethyl sulfoxide (DMSO, Sigma-Aldrich) to final concentrations of 0.25, 2.5, and 25 μM for PXR/Pxr-agonists, and 0.1, and 10 μM for BNF. 0.01% DMSO was used as solvent control in all exposures. Cytotoxicity of the chemicals was monitored by measuring the release of lactate dehydrogenase (LDH; EC 22.214.171.124) into the culture medium, using the LDH Cytotoxicity Detection KitPLUS (Roche Applied Sciences, Basel, Switzerland) according to the manufacturer’s protocol.
Total RNA was isolated from PCLS using the RNeasy Mini Kit (QIAGEN, Hilde, Germany). RNA concentration and RNA quality were assessed with a NanoDrop ND-1000 and agarose gel electrophoresis, and RNA was subsequently reverse transcribed to cDNA by either SuperScript III Reverse Transcriptase (Invitrogen, Thermo Fisher Scientific, Oslo, Norway) or qScript cDNA SuperMix (Quanta BioSciences, Gaithersburg, USA) following the producer’s protocol. The cDNA was diluted 1:30 in H2O prior to RT-qPCR using SYBR Green I Master (Roche) and the LightCycler® 480 Real-Time PCR System (Roche), according to the manufacturer’s procedure. Both a non-template control (H2O) and a positive control (calibrator cDNA) were included for each gene, and all samples were run in triplicates. The primers used for gene amplifications were synthesized by Sigma Aldrich (Supplementary Table 6). The transcriptional level of each gene was calculated using the Efficiency Calibrated Method of LightCycler® Software v1.5 (Roche), relating the expression to both a reference gene and a calibrator, and considering the efficiency of the reaction for each primer pair. Acidic ribosomal protein (arp) and ubiquitin (ubi) was used as reference genes82. Statistical analyses of RT-qPCR data were performed on Log2-converted relative gene expression in JMP v10 (SAS Institute) using Standard Least Squares with the fish individual as a random effect, followed by Tukey Kramer post hoc adjustment. Using this linear mixed-effects model, the variability of basal gene expression in individual fish is bypassed. Figures were prepared in Prism 6 (GraphPad), where the boxes represent the 25th to 75th percentile with the median indicated as a line and whiskers are drawn from the lowest to the highest value. Statistical significance (p < 0.05) between groups (control and two or three exposures groups) are marked by letters a, b, or c.
Promoter analysis of CYP3A and CYP1A orthologs
Four orthologs to the zebrafish cyp3a65 gene were identified in the ENSEMBL cod genome (‘gadMor1’) (Eide et al., in prep). These were confirmed in the new cod genome assembly33 and provided official names by the Cytochrome P450 Nomenclature Committee: cyp3a166 (location in ‘gadMor2’: LG03, base pairs 18402807-18400860), cyp3a167 (LG03, base pairs 18402807-18400860), cyp3a168P (LG03, base pairs 18384880-18386508), and cyp3a169 (LG01, base pairs 14702701-14723855). Genomic regions containing 13,000 base pairs of upstream sequences of cod cyp1a (LG14, base pairs 2303196-2307638), cyp3a166, and cyp3a169 were retrieved from the new genome assembly. The corresponding promoter regions of human CYP3A4 (ENSG00000160868), CYP1A1 (ENSG00000140465), and CYP1A2 (ENSG00000140505); mouse Cyp3a11 (ENSMUSG00000056035), Cyp1a1 (ENMUSG00000032315), and Cyp1a2 (ENSMUSG00000032310); and zebrafish cyp3a65 (ENSDARG00000103295), and cyp1a (ENSDARG00000098315), were all derived from ENSEMBL.
Potential nuclear receptor response elements in the upstream regions were predicted using the nuclear hormone receptor (NHR)-scan available online83. NHR-scan uses a HMM framework for describing binding behavior according to three ‘match state chains’, corresponding to site configurations of direct repeats, inverted repeats, and everted repeats, compared to a background state83. We used the default settings with 0.01 probability of entering each of the match states. The extended Ahr-binding XREs were mapped by searching the sequences for the consensus sequence ‘KNGCGTGM’37 in forward, reverse and complementary directions. The resulting response elements were visualized in Adobe Illustrator CS5 (v15.0.0), and horizontal slice diagrams of binding site distributions were prepared in Prism 6 (GraphPad).
Near, T. J. et al. Resolution of ray-finned fish phylogeny and timing of diversification. Proceedings of the National Academy of Sciences of the United States of America 109, 13698–13703 (2012).
Nelson, J. S. Fishes of the world, xix, 601 p. (John Wiley, Hoboken, N.J., 2006).
Goldstone, J. V. et al. The chemical defensome: Environmental sensing and response genes in the Strongylocentrotus purpuratus genome. Developmental Biology 300, 366–384 (2006).
Goldstone, J. V. Environmental sensing and response genes in cnidaria: the chemical defensome in the sea anemone Nematostella vectensis. Cell Biology and Toxicology 24, 483–502 (2008).
Stegeman, J. J., Goldstone, J. V. & Hahn, M. E. Perspectives on zebrafish as a model in environmental toxicology. In Fish physiology: Zebrafish (Elsevier, 2010).
van Denderen, P. D., Lindegren, M., MacKenzie, B. R., Watson, R. A. & Andersen, K. H. Global patterns in marine predatory fish. Nat Ecol Evol 2, 65–70 (2018).
Star, B. et al. The genome sequence of Atlantic cod reveals a unique immune system. Nature 477, 207–210 (2011).
Hasselberg, L., Meier, S., Svardal, A., Hegelund, T. & Celander, M. C. Effects of alkylphenols on CYP1A and CYP3A expression in first spawning Atlantic cod (Gadus morhua). Aquatic Toxicology 67, 303–313 (2004).
Sundt, R. C. & Björkblom, C. Effects of produced water on reproductive parameters in prespawning Atlantic cod (Gadus morhua). Journal of Toxicology and Environmental Health Part A: Current Issues 74, 543–554 (2011).
Eide, M., Karlsen, O.A., Kryvi, H., Olsvik, P.A. & Goksøyr, A. Precision-cut liver slices of Atlantic cod (Gadus morhua): An in vitro system for studying the effects of environmental contaminants. Aquatic Toxicology (2014).
Olsvik, P. A. et al. Are Atlantic Cod in Store Lungegrdsvann, a Seawater Recipient in Bergen, Affected by Environmental Contaminants? A qRT-PCR Survey. Journal of Toxicology and Environmental Health-Part a-Current Issues 72, 140–154 (2009).
Goksøyr, A. Purification of hepatic microsomal cytochromes P-450 from ß-naphthoflavone-treated Atlantic cod (Gadus morhua), a marine teleost fish. Biochimica et Biophysica Acta 840, 409–417 (1985).
Goksøyr, A. et al. Species characteristics of the hepatic xenobiotic and steroid biotransformation systems of 2 teleost fish, Atlantic cod (Gadus morhua) and Rainbow trout (Salmo-Gairdneri). Toxicology and Applied Pharmacology 89, 347–360 (1987).
Goksøyr, A., Solbakken, J. E. & Klungsøyr, J. Regioselective metabolism of phenanthrene in Atlantic cod (Gadus morhua) - Studies on the effects of monooxygenase inducers and role of cytochromes P-450. Chemico-Biological Interactions 60, 247–263 (1986).
Goksøyr, A., Serigstad, B., Solberg, T. S. & Stegeman, J. J. Response of cod (Gadus morhua) larvae and juveniles to oil exposure detected with anti-cod cytochrome P-450c IgG and anti-scup cytochrome P-450E MAb 1-12-3. Mar. Environ. Res. 24, 31–36 (1988).
Karlsen, O. A., Puntervoll, P. & Goksøyr, A. Mass spectrometric analyses of microsomal cytochrome P450 isozymes isolated from beta-naphthoflavone-treated Atlantic cod (Gadus morhua) liver reveal insights into the cod CYPome. Aquatic Toxicology 108, 2–10 (2012).
Germain, P., Staels, B., Dacquet, C., Spedding, M. & Laudet, V. Overview of nomenclature of nuclear receptors. Pharmacological Reviews 58, 685–704 (2006).
Ekins, S., Reschly, E.J., Hagey, L.R. & Krasowski, M.D. Evolution of pharmacologic specificity in the pregnane X receptor. Bmc Evolutionary Biology 8 (2008).
Whitfield, G. K. et al. Cloning of a functional vitamin D receptor from the lamprey (Petromyzon marinus), an ancient vertebrate lacking a calcified skeleton and teeth. Endocrinology 144, 2704–2716 (2003).
Zhao, Y. B., Zhang, K., Giesy, J. P. & Hu, J. Y. Families of Nuclear Receptors in Vertebrate Models: Characteristic and Comparative ToxicologicalPerspective. Scientific Reports 5 (2015).
Handschin, C., Podvinec, M. & Meyer, U. A. CXR, a chicken xenobiotic-sensing orphan nuclear receptor, is related to both mammalian pregnane X receptor (PXR) and constitutive androstane receptor (CAR). Proceedings of the National Academy of Sciences of the United States of America 97, 10769–10774 (2000).
Mathäs, M. et al. Evolutionary History and Functional Characterization of the Amphibian Xenosensor CAR. Molecular Endocrinology 26, 14–26 (2012).
Bertrand, S. et al. Unexpected novel relational links uncovered by extensive developmental profiling of nuclear receptor expression. Plos Genetics 3, 2085–2100 (2007).
Moore, L. B. et al. Pregnane X receptor (PXR), constitutive androstane receptor (CAR), and benzoate X receptor (BXR) define three pharmacologically distinct classes of nuclear receptors. Molecular Endocrinology 16, 977–986 (2002).
Goksøyr, A. Use of cytochrome P450 1A (CYP1A) in fish as a biomarker of aquatic pollution. Arch Toxicol Suppl 17, 80–95 (1995).
Tseng, H. P., Hseu, T. H., Buhler, D. R., Wang, W. D. & Hu, C. H. Constitutive and xenobiotics-induced expression of a novel CYP3A gene from zebrafish larva. Toxicology and Applied Pharmacology 205, 247–258 (2005).
Chang, C. T. et al. Regulation of zebrafish CYP3A65 transcription by AHR2. Toxicology and Applied Pharmacology 270, 174–184 (2013).
Kubota, A. et al. Role of Pregnane X Receptor and Aryl Hydrocarbon Receptor in Transcriptional Regulation of pxr, CYP2, and CYP3 Genes in Developing Zebrafish. Toxicological Sciences 143, 398–407 (2015).
Malmstrøm, M. et al. Evolution of the immune system influences speciation rates in teleost fishes. Nature Genetics 48, 1204–1210 (2016).
Malmstrøm, M., Matschiner, M., Tørresen, O. K., Jakobsen, K. S. & Jentoft, S. Whole genome sequencing data and de novo draft assemblies for 66 teleost species. Sci Data 4, 160132 (2017).
Krasowski, M. D., Ni, A., Hagey, L. R. & Ekins, S. Evolution of promiscuous nuclear hormone receptors: LXR, FXR, VDR, PXR, and CAR. Molecular and Cellular Endocrinology 334, 39–48 (2011).
Grün, F. et al. Benzoate X receptors alpha and beta are pharmacologically distinct and do not function as xenobiotic receptors. Journal of Biological Chemistry 277, 43691–43697 (2002).
Tørresen, O. K. et al. An improved genome assembly uncovers prolific tandem repeats in Atlantic cod. BMC Genomics 18, 95 (2017).
Qiu, H. et al. The unique complexity of the CYP3A4 upstream region suggests a nongenetic explanation of its expression variability. Pharmacogenetics and Genomics 20, 167–178 (2010).
Lusska, A., Shen, E. & Whitlock, J. P. Protein-DNA Interactions at a Dioxin-Responsive Enhancer - Analysis of 6 Bona-Fide DNA-Binding Sites for the Liganded Ah Receptor. Journal of Biological Chemistry 268, 6575–6580 (1993).
Sun, Y. V., Boverhof, D. R., Burgoon, L. D., Fielden, M. R. & Zacharewski, T. R. Comparative analysis of dioxin response elements in human, mouse and rat genomic sequences. Nucleic Acids Research 32, 4512–4523 (2004).
ZeRuth, G. & Pollenz, R. S. Functional analysis of cis-regulatory regions within the dioxin-inducible CYP1A promoter/enhancer region from zebrafish (Danio rerio). Chemico-Biological Interactions 170, 100–113 (2007).
Michalets, E. L. Update: Clinically significant cytochrome P-450 drug interactions. Pharmacotherapy 18, 84–112 (1998).
Lee, S. J. & Buhler, D. R. Cloning, tissue distribution, and functional studies of a new cytochrome P450 3A subfamily member, CYP3A45, from rainbow trout (Oncorhynchus mykiss) intestinal ceca. Archives of Biochemistry and Biophysics 412, 77–89 (2003).
Kullman, S. W., Hamm, J. T. & Hinton, D. E. Identification and characterization of a cDNA encoding cytochrome P450 3A from the fresh water teleost medaka (Oryzias latipes). Archives of Biochemistry and Biophysics 380, 29–38 (2000).
Vaccaro, E. et al. Cloning, tissue expression, and inducibility of CYP 3A79 from sea bass (Dicentrarchus labrax). Journal of Biochemical and Molecular Toxicology 21, 32–40 (2007).
Christen, V., Caminada, D., Arand, M. & Fent, K. Identification of a CYP3A form (CYP3A126) in fathead minnow (Pimephales promelas) and characterisation of putative CYP3A enzyme activity. Analytical and Bioanalytical Chemistry 396, 585–595 (2010).
Ma, J. G., Bu, Y. Z., Li, Y., Niu, D. C. & Li, X. Y. Complementary DNA Cloning and Functional Characterization of Cytochrome P450 3A138 in Common Carp (Cyprinus carpio L.). Journal of Biochemical and Molecular Toxicology 28, 239–245 (2014).
Sun, A. R. et al. Molecular cloning and expression analysis of cytochrome P450 3A gene in the turbot Scophthalmus maximus. Fish Physiology and Biochemistry 39, 1239–1251 (2013).
Celander, M. & Stegeman, J. J. Isolation of a cytochrome P450 3A cDNA sequence (CYP3A30) from the marine teleost Fundulus heteroclitus and phylogenetic analyses of CYP3A genes. Biochemical and Biophysical Research Communications 236, 306–312 (1997).
Bresolin, T., Rebelo, M. D. & Bainy, A. C. D. Expression of PXR, CYP3A and MDR1 genes in liver of zebrafish. Comparative Biochemistry and Physiology C-Toxicology & Pharmacology 140, 403–407 (2005).
Wassmur, B., Grans, J., Kling, P. & Celander, M. C. Interactions of pharmaceuticals and other xenobiotics on hepatic pregnane X receptor and cytochrome P450 3A signaling pathway in rainbow trout (Oncorhynchus mykiss). Aquatic Toxicology 100, 91–100 (2010).
Grans, J. et al. Regulation of pregnane-X-receptor, CYP3A and P-glycoprotein genes in the PCB-resistant killifish (Fundulus heteroclitus) population from New Bedford Harbor. Aquatic Toxicology 159, 198–207 (2015).
Yan, J. & Cai, Z. H. Molecular Evolution and Functional Divergence of the Cytochrome P450 3 (CYP3) Family in Actinopterygii (Ray-Finned Fish). Plos One 5 (2010).
Shaya, L., Dejong, C. & Wilson, J. Y. Expression patterns of cytochrome P450 3B and 3C genes in model fish species. Comparative Biochemistry and Physiology C-Toxicology & Pharmacology 166, 115–125 (2014).
Corley-Smith, G. E. et al. CYP3C1,the first member of a new cytochrome P450 subfamily found in zebrafish (Danio rerio). Biochemical and Biophysical Research Communications 340, 1039–1046 (2006).
Milnes, M. R. et al. Activation of steroid and xenobiotic receptor (SXR, NR1I2) and its orthologs in laboratory, toxicologic, and genome model species. Environmental Health Perspectives 116, 880–885 (2008).
Husøy, A. M. et al. Immunohistochemical localization of Cyp1a-like and Cyp3a-like isozymes in hepatic and extrahepatic tissues of Atlantic cod (Gadus morhua l), a marine fish. Toxicology and Applied Pharmacology 129, 294–308 (1994).
Staudinger, J., Liu, Y. P., Madan, A., Habeebu, S. & Klaassen, C. D. Coordinate regulation of xenobiotic and bile acid homeostasis by pregnane X receptor. Drug Metabolism and Disposition 29, 1467–1472 (2001).
Bizarro, C., Eide, M., Hitchcock, D. J., Goksoyr, A. & Ortiz-Zarragoitia, M. Single and mixture effects of aquatic micropollutants studied in precision-cut liver slices of Atlantic cod (Gadus morhua). Aquatic Toxicology 177, 395–404 (2016).
Hasselberg, L., Grøsvik, B. E., Goksøyr, A. & Celander, M. C. Interactions between xenoestrogens and ketoconazole on hepatic CYP1A and CYP3A, in juvenile Atlantic cod (Gadus morhua). Comp Hepatol 4, 2 (2005).
Meucci, V. & Arukwe, A. The xenoestrogen 4-nonylphenol modulates hepatic gene expression of pregnane X receptor, aryl hydrocarbon receptor, CYP3A and CYP1A1 in juvenile Atlantic salmon (Salmo salar). Comparative Biochemistry and Physiology C-Toxicology & Pharmacology 142, 142–150 (2006).
Ohtake, F. et al. Dioxin receptor is a ligand-dependent E3 ubiquitin ligase. Nature 446, 562–566 (2007).
Aranda, A. & Pascual, A. Nuclear hormone receptors and gene expression. Physiological Reviews 81, 1269–1304 (2001).
Laudet, V. & Gronemeyer, H. The Nuclear Receptor FactsBook, (Gulf Professional Publishing, 2002).
Quattrochi, L. C. & Guzelian, P. S. CYP3A regulation: From pharmacology to nuclear receptors. Drug Metabolism and Disposition 29, 615–622 (2001).
Nakata, K., Tanaka, Y., Nakano, T. & Adachi, T. Nuclear receptor-mediated transcriptional regulation in phase I, II, and III xenobiotic metabolizing systems. Drug Metabolism and Pharmacokinetics 21, 437–457 (2006).
Goodwin, B., Hodgson, E. & Liddle, C. The orphan human pregnane X receptor mediates the transcriptional activation of CYP3A4 by rifampicin through a distal enhancer module. Molecular Pharmacology 56, 1329–1339 (1999).
Barwick, J. L. et al. Trans-species gene transfer for analysis of glucocorticoid-inducible transcriptional activation of transiently expressed human CYP3A4 and rabbit CYP3A6 in primary cultures of adult rat and rabbit hepatocytes. Molecular Pharmacology 50, 10–16 (1996).
Liu, F. J., Song, X., Yang, D., Deng, R. & Yan, B. The far and distal enhancers in the CYP3A4 gene co-ordinate the proximal promoter in responding similarly to the pregnane X receptor but differentially to hepatocyte nuclear factor-4 alpha. Biochemical Journal 409, 243–250 (2008).
Inoue, S. I., Yoshinari, K., Sugawara, M. & Yamazoe, Y. Activated Sterol Regulatory Element-Binding Protein-2 Suppresses Hepatocyte Nuclear Factor-4-Mediated Cyp3a11 Expression in Mouse Liver. Molecular Pharmacology 79, 148–156 (2011).
Hines, R. N., Mathis, J. M. & Jacob, C. S. Identification of Multiple Regulatory Elements on the Human Cytochrome P450ia1 Gene. Carcinogenesis 9, 1599–1605 (1988).
Hektoen, H., Bernhoft, A., Ingebrigtsen, K., Skaare, J. U. & Goksoyr, A. Response of Hepatic Xenobiotic-Metabolizing Enzymes in Rainbow-Trout (Oncorhynchus-Mykiss) and Cod (Gadus-Morhua) to 2,3,7,8-Tetrachlorodibenzo-P-Dioxin (2,3,7,8-Tcdd). Aquatic Toxicology 28, 97–106 (1994).
Larsen, B. K. et al. Comparison of protein expression in plasma from nonylphenol and bisphenol A-exposed Atlantic cod (Gadus morhua) and turbot (Scophthalmus maximus) by use of SELDI-TOF. Aquatic Toxicology 78, S25–S33 (2006).
Aitken, A. E., Richardson, T. A. & Morgan, E. T. Regulation of drug-metabolizing enzymes and transporters in inflammation. Annual Review of Pharmacology and Toxicology 46, 123–149 (2006).
Morgan, E. T. Regulation of cytochromes P450 during inflammation and infection. Drug Metabolism Reviews 29, 1129–1188 (1997).
Goralski, K. B., Abdulla, D., Sinal, C. J., Arsenault, A. & Renton, K. W. Toll-like receptor-4 regulation of hepatic Cyp3a11 metabolism in a mouse model of LPS-induced CNS inflammation. American Journal of Physiology-Gastrointestinal and Liver Physiology 289, G434–G443 (2005).
Teng, S. & Piquette-Miller, M. The involvement of the pregnane X receptor in hepatic gene regulation during inflammation in mice. Journal of Pharmacology and Experimental Therapeutics 312, 841–848 (2005).
Zhou, C., Verma, S. & Blumberg, B. The steroid and xenobiotic receptor (SXR), beyond xenobiotic metabolism. Nucl Recept Signal 7, e001 (2009).
Xie, W. & Tian, Y. N. Xenobiotic receptor meets NF-kappa B, a collision in the small bowel. Cell Metabolism 4, 177–178 (2006).
Zhou, C. et al. Mutual repression between steroid and xenobiotic receptor and NF-kappa B signaling pathways links xenobiotic metabolism and inflammation. Journal of Clinical Investigation 116, 2280–2289 (2006).
Malmstrøm, M., Jentoft, S., Gregers, T. F. & Jakobsen, K. S. Unraveling the Evolution of the Atlantic Cod’s (Gadus morhua L.) Alternative Immune Strategy. Plos One 8 (2013).
Solbakken, M.H. et al. Evolutionary redesign of the Atlantic cod (Gadus morhua L.) Toll-like receptor repertoire by gene losses and expansions. Scientific Reports 6 (2016).
Finn, R. D. et al. Pfam: the protein families database. Nucleic Acids Research 42, D222–D230 (2014).
Ronquist, F. & Huelsenbeck, J. P. MrBayes 3: Bayesian phylogenetic inference under mixed models. Bioinformatics 19, 1572–1574 (2003).
Rose, T. M., Henikoff, J. G. & Henikoff, S. CODEHOP (COnsensus-DEgenerate Hybrid Oligonucleotide Primer) PCR primer design. Nucleic Acids Res 31, 3763–6 (2003).
Olsvik, P. A., Søfteland, L. & Lie, K. K. Selection of reference genes for qRT-PCR examination of wild populations of Atlantic cod (Gadus morhua). BMC Res. Notes 1, 47 (2008).
Sandelin, A. & Wasserman, W. W. Prediction of nuclear hormone receptor response elements. Molecular Endocrinology 19, 595–606 (2005).
The work was supported by the Research Council of Norway (RCN) as part of the iCOD and iCOD 2.0 (grant no. 192441/I30 and 244654/E40) to AG and OAK, dCod 1.0 (248840 projects) to AG, and the National Institute of Health (USA) NIH P42ES007381 (Boston University Superfund Center), and NIH R21HD073805 grants to JVG and JS. Support for teleost genome sequencing and analyses has been through RCN funding (grant no. 222378) to KSJ. The sequencing towards the new Atlantic cod reference genome was provided by the Norwegian Sequencing Centre (www.sequencing.uio.no), a national technology platform hosted by the University of Oslo and supported by the “Functional Genomics” and “Infrastructure” programs of the Research Council of Norway and the Southeastern Regional Health Authorities.
The authors declare no competing interests.
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Eide, M., Rydbeck, H., Tørresen, O.K. et al. Independent losses of a xenobiotic receptor across teleost evolution. Sci Rep 8, 10404 (2018). https://doi.org/10.1038/s41598-018-28498-4
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