1. Introduction
Aquaculture industry is rapidly expanding and becoming more intensified in order to meet the increased global demand for fish protein [
1,
2]. This intensification of production may bring about impairments in health and growth performance [
3,
4,
5], which has contributed to increase the ethical concerns of the consumers on aquaculture welfare issues [
6,
7]. In that sense, it is essential that the monitoring of welfare status might cover a wide-range of welfare indicators, either input-based, referring to the conditions in which the animals are subjected, or outcome-based, which reflect the degree of fulfilment of their welfare needs [
8,
9,
10]. Examples of the first type of indicators are stocking density or water oxygen concentration and temperature, whereas growth performance, survival rates, external appearance (skin/fin erosion), sex ratio or maturation state are outcome-based indicators. Another approach for classifying welfare indicators is to divide them by whether they are practical and easy to use on a farm (operational welfare indicators, OWIs), or complex and difficult without access to a laboratory for evaluation (laboratory welfare indicators, LABWIs). However, the range and diversity of welfare needs are constantly evolving as more knowledge and new technologies become available. In that sense, it is noteworthy that common measurements of cortisol on blood plasma are now moving towards other target tissues (e.g., faeces, scales and mucus) [
11] to minimize large variability and dramatic increases by the sampling itself in the aquatic environment [
12,
13], though each target tissue would provide different information on the welfare state and particularly on the timing of the stress response. Likewise, behavioural monitoring is often difficult in the aquatic environment [
14,
15], but the use of miniaturized data-loggers externally attached to the operculum of sentinel fish represent a practical solution for a continuous and accurate individual tracking of swimming activity and breathing rates in tank-based rearing systems [
16].
The monitoring of the microorganisms living in or around the farmed animals is also a very promising aquaculture welfare indicator that can serve to plan corrective actions to mitigate an environmental issue, or to modulate the physiological state and the response of the organism from a holobiont perspective [
17]. Thus, experimental evidence supports the use of some bacteria taxa as strong markers of thermal stress [
18,
19] or microplastic exposure [
20,
21] in both salmonid and non-salmonid fish, which could be monitored in a real time and in a cost-effective manner with the advent of the 16S metabarcoding techniques based on the Nanopore technology [
22,
23], though we are far to establish references values for a wide spectrum of species and culture condition across the production cycle [
24,
25]. Other welfare indicators that can aid in developing an improved welfare assessment system are those based on age-related cellular and molecular modifications. Certainly, age-associated DNA methylation changes allow the construction of extremely accurate age estimators, termed “epigenetic” or “DNA methylation” clocks, which have been developed for a number of vertebrates, including mammals, birds and fish [
26,
27,
28]. Thus, several piscine DNA methylation clocks have been built, to be applied in fisheries and conservation biology programs, with a focus on searching CpGs that mostly reflect the chronological age [
28]. Nevertheless, many age-related epigenetic variations are also sensitive to environmental influences [
29], either in mammals [
30] or fish [
31], and there is accumulating evidence that, depending on the CpG loci used, epigenetic clocks can inform not only about chronological but also biological age [
32,
33,
34], which bring the possibility of a high resolution and precise understanding of the age-related pathology and physiology of an individual [
35,
36].
According to the above findings, epigenetic markers of biological age have been proposed as reliable markers of cumulative welfare in animal production [
37,
38,
39,
40]. However, the integration of data from more than one omics layer will add potential value to the measure [
34,
41], and the combination of transcriptomic and DNA methylation data may link in a more precise manner age-regulated epigenetic marks with specific cellular functions or fitness traits [
41,
42]. This also applies to fish, and such integrative omic approach has been used in gilthead sea bream to evaluate the success of nutritional programming in the offspring of broodstock fish fed low fish meal/fish oil diets [
43], to reveal genotype-by-temperature interactions in male sex determination and spermatogenesis in zebrafish [
44], or to better understand the challenge of moderate hypoxia and temperature increases in Atlantic salmon [
45]. Likewise, a targeted transcriptomic/epigenetic approach have disclosed the use of the changing gene expression and DNA methylation pattern of sirtuin 1 as a marker of age- and seasonally-mediated changes of energy metabolism in the skeletal muscle of gilthead sea bream [
46]. However, to the best of our knowledge, the integration of wide transcriptomic and DNA methylation data as markers of biological age remains to be largely explored in farmed fish, though experimental evidence highly supported a strong effect of main aquaculture stressors on several biological functions [
47,
48], through epigenetic marks preferentially located at the gene-promoter regulatory regions [
49,
50,
51]. In agreement with all this, our starting hypothesis was that the integration of wide transcriptomic and epigenomic approaches, filtered by the involvement in multiple functions and differentially methylated CpGs in the gene-promoter regulatory region, would provide a list of putative gene markers of biological age for an extended and precise assessment of cumulative fish welfare. For that purpose, massive gene expression analysis (RNA-seq) combined with a genome-wide DNA methylation (MBD-seq) approach was conducted to disclose the different omics multilayer of white skeletal muscle in one- and three-year old gilthead sea bream, the most highly cultured fish in the Mediterranean region. This allowed to identify up to 10 age-regulated genes, with particular epigenetic marks and multifunction capabilities, as an array of potential biological age gene markers that will require to be further validated in independent studies.
3. Discussion
Refining approaches to safeguard and optimise the wellbeing of fish can help to increase the profitability and sustainability of aquaculture through the production of more robust fish. There is now a vast array of fish welfare indicators, but there is little consensus on the most adequate criteria to evaluate differences in welfare needs among species, rearing systems or biological features [
52,
53]. Thus, in the gonochoristic teleost European sea bass, elevated temperatures during early development (thermosensitive period) resulted in a masculinization of the population [
54,
55]. Conversely, an accelerated male-female sex reversal in the protandrous hermaphrodite gilthead sea bream seems to be the phenotypic expression of a cumulative impaired welfare that is both nutritionally and genetically regulated [
56,
57]. This latter process exemplifies a biological age deviation as the result of a pseudo-feminization process with a lowered estradiol/11ketosterone plasma ratio in reproductive females, which would denote a failure of the negative feedback inhibition of male-female sex reversal. Likewise, at a cellular and molecular level, the present study disclosed a vast number of age-regulated muscle transcripts by comparing one- and three-year old fish with homogeneous weights within groups and with no sex bias. Indeed, in the hermaphrodite gilthead sea bream nearly all one-year old fish are usually males and in this work the three-year old fish employed for sampling had a similar weight of around 1 kg, as expected for males at that age compared to the heavier females when fed a control diet with high levels of fish meal and fish oil [
57]. Overall, this study finally allowed to obtain an enriched list of 10 candidate markers of biological aging after the integration of two omics layers (transcriptomics and epigenetics) and filtering by multifunctional genes with DM CpGs in regulatory regions, which will require a final functional validation in independent studies.
Age-mediated shifts in gene expression have been reported in numerous species [
58,
59], though the type of genes that are regulated vary among different tissues and organisms [
60]. Accordingly, a clear impact of age on the muscle transcriptome was observed in the current study (
Figure 1), which is consistent with previous studies in mammals [
61,
62] and fish [
63,
64]. Moreover, we observed that most discriminant coding DE transcripts were down-regulated with advancing age, which would reflect the normal declining with age of a wide-range of biological processes [
59,
65,
66], though paradoxically it is not the common feature in a number of previous studies in mammals and fish [
61,
62,
64]. In any case, it is well accepted that aging is related, in mammals [
67] and fish (killifish) used a model of vertebrate aging, with an overall hypomethylation that becomes first associated to a down-regulation of DNA methyltransferases. In the present study, this fits well with a global hypo-methylation (58.5 %) among the discriminant DM regions in our age model of one- and three-year old fish, that at the same time would co-exist with a site-specific hypermethylation, as reported upon aging in both humans [69] and other animal models [67,70], including fish [28,71,72].
Methylation of DNA is usually associated with the silencing of gene expression [73]. Nonetheless, as mentioned before, most DE genes presented a lowered expression with age regardless of methylation pattern. Certainly, two different types of transcriptomic and epigenetic interplays were found herein with the age-related down-regulated gene expression. Accordingly, a first set of transcripts presented an opposite trend for DNA methylation and expression (33 transcripts and UD), which means that they showed a down-regulated expression due to hyper-methylation (24 transcripts) or vice versa (9 transcripts), resulting in a significant negative correlation between DNA methylation and their expression level (
Figure 4A). Conversely, a second group of 61 down-regulated transcripts (57 UD) were linked to hypo-methylated DM regions. The effect of the differential methylation on gene expression may rely on the position of the epigenetic mark because increased methylated CpG sites in the promoter region of a gene results normally in shutdown of its expression [74,75,76]. Likewise, methylation of the first exon/intron may be also strongly related to the transcriptional silencing [77,78]. Nevertheless, DNA methylation patterns are far more complex than originally thought. For instance, hypo-methylation does not seem to be always an activating epigenetic change, since the loss of DNA methylation in the gene body may be accompanied by formation of repressive chromatin, resulting in a decreased expression [79]. Alternatively, a lower methylation level at gene bodies may result in gene silencing due to nucleosome destabilization in transcribed regions and reduced efficiencies of transcription elongation or splicing [80,81]. This hypo-methylation-induced gene expression shutdown might contribute to a certain degree of instability in the chromatin or nucleosome, which could explain the less clear pattern on the effect of the reduced level of methylation in this second set of retained transcripts (
Figure 4B) and suggests that this impact seems to be less reproducible and reliable. Hence, only the transcripts of the first group, whose changes in expression are likely a result of the direct action of enzymes involved in the DNA methylation or demethylation, were kept herein for further selection.
Among the 33 transcripts presenting an opposite trend for DNA methylation and expression, those linked to a greater number of processes (>4 GO-BP ancestors) were retained as a first list of selected markers. Such filtering approach rendered 14 multiple function genes that would be more likely affected by environmental insults (e.g., increased temperatures and hypoxia), which in turn serves to disclose a set of molecular markers that become potentially highly responsive to aging and common aquaculture stressors [47,48,82,83]. In that sense, it must be noted that the resulting list of selected genes are largely involved in developmental processes, which agrees with the fact that aging is viewed as an evolutionary conserved developmental process across mammals [84], and vertebrates in general. Moreover, the observation that most of the above selected genes (10 out of 14; 71%) shared a DM region in their promoter regulatory region further supports a physiological role as age-related markers of environmental perturbations [
49,
50,
51], which makes our final set of 10 genes a reliable list of candidate markers of chronological age deviations.
From a functional point of view, it must be noted that the suppression of cellular senescence by SIRTs is mainly mediated through delaying the age-related telomere attrition, sustaining genome integrity, and promoting DNA damage repair [85,86,87,88]. Certainly, the increasing evidence of SIRTs in the field of aging and age-related diseases indicates that they may provide novel targets for treating diseases associated with aging and extended human lifespan [89]. This becomes especially evident for SIRT1, the most extensively studied mammalian SIRT. In that sense, the observation that the gene
sirt1 is included in our final list of biological markers confirms and extend our previous gilthead sea bream study, in which muscle
sirt1 was shaped by age at the transcriptional and epigenetic level in a farmed fish trough the production cycle [
46]. Moreover, this outcome served as a methodological checkpoint of the procedure that we have used herein for revealing potential markers of chronological age that at the same time have the potential to be regulated at a large extent by a challenging environment. Regarding the gene
psmd2 (26S proteasome non-ATPase regulatory subunit 2), it encodes for one of the non-ATPase subunits of the 19S regulator lid within the 26S proteasome, a multicatalytic proteinase complex that is involved in the ubiquitin–proteasome system, recognised as a major intracellular protein degradation system with an important role for muscle homeostasis and health [90]. It has been suggested that proteasome activity decreases with age in several tissues [91,92], including skeletal muscle [93]. Nevertheless, proteasomes might play a relevant role in DNA damage signaling and DNA repair [94], as previously indicated for SIRTs, and this
psmd2 gene may be involved in cell cycle and increase cell proliferation [95], which might be related to the high levels of
psmd2 significantly associated with age [95] and explain its up-regulation in our model of older fish.
Other two sets of genes with a complementary role with aging are those of bmp1 - smad1 and ramp1- calcrl. First, bmp1 (Bone morphogenetic protein 1) encodes for one of the bone morphogenetic proteins (BMP) that bind to dedicated receptors that in turn phosphorylate BMP-responsive Smad proteins (e.g., Smad1 encoded by gene smad1, mothers against decapentaplegic homolog 5) [96]. BMP signalling is indispensable for the regulation of adult muscle mass in normal and pathological situations [97]. So, it may be speculated that the down-regulation of bmp1 might be related to the progressive reduction in muscle mass with age [98,99], whereas smad1 is up-regulated to maximize the use of the available BMP. The other two linked genes, calcrl (Calcitonin gene-related peptide type 1 receptor-like) and ramp1 (Receptor activity-modifying protein 1), encode for two components of G protein-coupled receptors, specifically the calcitonin receptor-like receptor and a receptor activity-modifying protein, respectively. These receptors mediate the effects of peptide hormones, such as calcitonin gene related peptide (CGRP), which play important roles during adulthood and aging, particularly in the neuromuscular system [100,101]. Indeed, in skeletal muscle, CGRP has been shown to potentiate muscle contraction [102] and increase the rate of blood flow locally following muscle contraction [103,104,105]. In the present study, the expression of calcrl is down-regulated and that of ramp1, up-regulated with age. Thus, it may be proposed that increased transcription of ramp1 might be an effective strategy for increasing the effectiveness of CGRP-induced effects [106], so its expression may be increased with age to compensate the reduction in calcrl transcription. Another down-regulated gene was thrb (Thyroid hormone receptor beta), which encodes for a nuclear hormone receptor for thyroid hormones that participate in skeletal muscle contractile function, myogenesis and muscle regeneration [107]. Thus, its down-regulation may be related to the progressive decline in muscle activity with age [98,99,108].
In our experimental model, another candidate marker that was down-regulated with advancing age is col5a1, (collagen alpha-1(V) chain). Collagen is the main structural protein in the extracellular matrix (ECM) of the skeletal muscle and it is essential for the mechanical support of tissue, although the gene expression of ECM components, including collagenic genes, decreases with age [63,109]. Likewise, the gene spred2 (Sprouty Related EVH1 Domain Containing 2) encodes for one of the proteins that regulate growth factor-induced activation of the mitogen-activated protein kinase (MAPK) cascade [110], which is considered a positive regulator of muscle atrophy [111]. Hence, the lower expression of this gene in older animals, and consequently a lower inhibition of MAPK, could be the cause of an increased muscle atrophy with age. Finally, atp1a2 (Sodium/potassium-transporting ATPase subunit alpha-2) is one of the genes encoding for different Na+, K+ ATPase (NKA) α-isoforms and is mainly expressed in muscle, either in mammals [112,113] or fish [114,115,116]. As a euryhaline teleost, gilthead sea bream may exhibit high NKA activity in seawater [117,118,119,120], and the lower expression of this gene might be linked with the reduction of ATPase activity in muscle with age [121].
In summary, as depicted in
Figure 5, an integrative approach of transcriptomics and DNA methylation data from one- and three-year old fish applied over successive selection steps allowed to generate a candidate list of muscle markers of biological age in farmed gilthead sea bream. Previous attempts of age-related markers in fisheries and conservation biology studies have been focused on chronological age markers, but in farmed animals attention is now moved towards indicators of the cumulative burden of environmental experiences, which may accelerate or decelerate the age progression along the production cycle. In comparison to common biomarkers of age, such as telomere length, DNA methylation marks have very often a better predictive ability [122], which would be reinforced herein by the integration of two omics layer (transcriptomics and epigenetics), followed by the use of successive filters to disclose age-related markers highly influenced by cumulative life insults. The result is a reduced list of 10 potential biological age markers that require to be validated in independent studies. Afterwards, the generated knowledge (i.e., the gene expression data from these biomarkers) might be applied through an appropriate estimation algorithm (e.g., multiple linear regression) [123,124] to compute individual’s biological age at a field scale as part of an improved welfare assessment system for auditing farmed fish welfare.
4. Materials and Methods
4.1. Ehics Statement
All procedures of animal rearing and sampling were carried out according to present IATS-CSIC Review Board, European animal directives (2010/63/EU), and Spanish laws (Royal Decree RD53/2013) for the protection of animals used in scientific experiments.
4.2. Experimental Setup
One- (S+1) and three- (S+3) year-old gilthead sea bream (GSB) of Atlantic origin were reared at the indoor experimental facilities of the Institute of Aquaculture Torre de la Sal (IATS-CSIC) in 3000-L tanks under natural photoperiod and temperature conditions at the IATS-CSIC latitude (40°5 N; 0°10E). Water temperature was between 23 and 28 °C in the summer when sampling was conducted, the water oxygen concentration was always higher than 75% saturation, and unionized ammonia remained below toxic levels (< 0.02 mg/L). Fish were fed a standard commercial diet (EFICO YM 568; BioMar, Dueñas, Spain) once a day until visual satiety (5 or 6 times per week depending on fish size). Seven fish per age class (one year old, S+1, 100–115 g body weight; three years old, S+3, 1 kg body weight) were anesthetized with 3-aminobenzoic acid ethyl ester (MS-222, 100 μg/mL), and white skeletal muscle (WSM) was rapidly excised, frozen in liquid nitrogen and stored at − 80 °C until RNA and DNA extraction.
4.3. DNA/RNA Extraction
White skeletal muscle DNA was extracted using the Quick-DNA™ Mini-prep Plus Kit (Zymo Research, Irvine, CA, USA) following the manufacturer’s instructions. The quantity and quality of DNA were assessed by a NanoDrop 2000cSpectrophotometer (Thermo Fisher Scientific, Waltham, MA, USA), and DNA integrity was assessed in a 1% agarose gel. Total RNA (70–100 μg) from WSM was extracted with the MagMAXTM-96 Total RNA Isolation Kit (Applied Biosystems, Foster City, CA, United States). The RNA concentration and purity were determined using a Nanodrop 2000c Spectrophotometer (Thermo Fisher Scientific, Waltham, MA, United States). Quality and integrity of the isolated RNA were checked on an Agilent Bioanalyzer 2100 total RNA Nano series II chip (Agilent, Amstelveen, Netherlands), yielding RNA integrity numbers (RINs) between 8 and 10. Samples were stored at -80 ºC until DNA and RNA sequencing.
4.4. DNA/RNA Illumina Sequencing
For the Methyl-binding domain sequencing (MBD-seq) analysis, 300 ng of DNA from S+1 and S+3 samples were fragmented to 200-550 pb using the methylation-insensitive restriction enzyme MseI (New England Biolabs, United States), which recognizes genomic T↓TAA sites, typically found outside of CGIs. The enzyme action and inactivation temperatures, as well as its actuation times and concentration were fixed according to manufacturer’s indications. Products were obtained using AMPure beads and checked and quantified with Picogreen (Invitrogen, Carlsbad, United States). Fragmented DNA was then submitted to methylation enrichment using the MethylCollectorTM Ultra kit (Active Motif, Carlsbad, CA, United States), following the instructions. Briefly, methylated DNA was captured from 75 ng of fragmented DNA via binding to the methyl-CpG binding domain of the MBD2 protein. Illumina MBD-seq libraries were prepared from 15 ng of methylated DNA fragments using the NEBNext® Ultra™ II DNA Library Prep Kit (Illumina Inc. San Diego, CA, USA) according to the manufacturer’s instructions. All libraries were sequenced on an Illumina NextSeq 500 HO sequencer as a 1 × 75 nucleotides single-end (SE) read format, according to the manufacturer’s protocol. Raw sequenced data were deposited in the Sequence Read Archive (SRA) of the National Center for Biotechnology Information (NCBI) under the Bioproject accession number PRJNA1096613 (BioSample accession numbers: SAMN40757284-297).
Illumina RNA-seq libraries were prepared from 500 ng total RNA using the Illumina TruSeq™ Stranded mRNA LT Sample Prep Kit (Illumina Inc. San Diego, CA, USA) according to the manufacturer’s instructions. All RNA-seq libraries were sequenced on an Illumina NextSeq 500 HO sequencer as 1 × 75 nucleotides SE read format according to the manufacturer’s protocol. Raw sequenced data were deposited in the Sequence Read Archive (SRA) of the National Center for Biotechnology Information (NCBI) under the Bioproject accession number PRJNA1096613 (BioSample accession numbers: SAMN40757298-311).
4.5. Bioinformatic Analyses
After sequencing, the quality of the RNA-seq and MBD-seq resulting raw reads was evaluated with FASTQC (
https://www.bioinformatics.babraham.ac.uk/projects/fastqc/). In the case of RNA-seq data, libraries were filtered with Prinseq [125] eliminating those with quality < 18, length < 60 bp, and > 5% of Ns in the sequence. Cleaned reads were mapped against gilthead sea bream reference genome [126] (available at
https://seabreamdb.nutrigroup-iats.org/), using TopHat [127]. A representative transcriptome per sample was constructed using Cufflinks, being data quality-checked with CummeRbund [128].
In the case of MBD-seq data, pre-processing was performed with Prinseq [125], eliminating those with quality < 20, length < 60 bp, and > 5% of Ns in the sequence. Before mapping, the repeat regions of the gilthead sea bream reference were masked using the BSgenome R package. Then, high-quality reads were aligned to this masked genome using the Bowtie2 software [129]. After MBD-seq mapping, the methylated reads were located in their corresponding genomic region using five training sets created ad-hoc for this analysis. The exon and intron training sets contained the coordinates of these elements along the genome. The promoter region of a gene was considered 5000 bp before its start codon. Finally, two training sets were established for CGI, depending on if these islands were found in promoters or intergenic regions. Predictions of CGI were done with NewCpGReport tool from the EMBOSS suite [130]. Search parameters for CGI were: length ≥ 200, C+G content ≥ 50%, ratio of observed/expected CpGs ≥ 0.60 and window size = 100.
4.6. Statistical Analysis and Data Filtering
DE transcripts in RNA-seq data were retrieved using DESeq2 at two significance thresholds (P < 0.05 and FDR < 0.05) [131]. DM regions in MBD-seq data were obtained using the MEDIPS R package (P < 0.05) [132] over regions of 25-bp size, containing at least one dinucleotide CG. To study the separation of the experimental groups, we performed several partial least-squares discriminant analyses (PLS-DA) using EZinfo v3.0 (Umetrics, Umeå, Sweden). DE transcripts and DM regions with a P < 0.05 were introduced in the analyses. The fitness and predictability of these models were validated by a 500 random permutation test (pR2Y < 0.05; pQ2 < 0.05) using the ropls R package [133]. The discriminant ability of each marker was ranked after the creation of the models according to its Variable Importance in the Projection (VIP), and useful markers were detected under a VIP ≥ 1 [134]. Discriminant DE transcripts were matched with those transcripts containing discriminant DM regions (multiomic layer integration) and different bioinformatic analysis and filters (i.e., functional GO enrichment, integrative correlation analysis, multifunction filtering, regulatory region – either promoter, first intron or first exon – filter) were applied over the obtained overlapping transcripts (
Figure 6) in order to obtain the list of candidate biological age markers. Over-representation tests of GO-BP terms was implemented in the ShinyGO 0.77 web application [135] and statistical significance was accepted at FDR < 0.05. GO-BP levels and supra-categories were retrieved using GOATools [136]. Pearson correlation coefficients between the expression and methylation Log2FC were performed using the SigmaPlot v14.5 (Systat Software Inc.) software. Gene structure representations were obtained using the genemodel R package (
https://github.com/greymonroe/genemodel) and the IBS software [137].
Figure 1.
(A) Differentially expressed (DE) transcripts between one- (S+1) and three-year old fish (S+3). Numbers indicate DE transcripts (based on One-way ANOVA P<0.05 or FDR-adjusted P < 0.05, in brackets). (B) Scores plot of partial least-squares discriminant analysis (PLS-DA) of muscular transcripts from S+1 and S+3 animals. RNA-seq data in the analysis were normalized values of differentially expressed transcripts (One-way ANOVA, P < 0.05). (C) Heatmap showing the abundance distribution (z-score) of the DE genes identified to be driving the separation between age groups.
Figure 1.
(A) Differentially expressed (DE) transcripts between one- (S+1) and three-year old fish (S+3). Numbers indicate DE transcripts (based on One-way ANOVA P<0.05 or FDR-adjusted P < 0.05, in brackets). (B) Scores plot of partial least-squares discriminant analysis (PLS-DA) of muscular transcripts from S+1 and S+3 animals. RNA-seq data in the analysis were normalized values of differentially expressed transcripts (One-way ANOVA, P < 0.05). (C) Heatmap showing the abundance distribution (z-score) of the DE genes identified to be driving the separation between age groups.
Figure 2.
(A) Differentially methylated (DM) regions between one- (S+1) and three-year old fish (S+3). Numbers indicate DM regions (based on One-way ANOVA P<0.05 or FDR-adjusted P < 0.05, in brackets). (B) Scores plot of partial least-squares discriminant analysis (PLS-DA) of muscular methylated regions from S+1 and S+3 animals. MBD-seq data were the normalized values of differentially methylated 25-bp genomic regions (One-way ANOVA, P < 0.05). (C) Heatmap showing the abundance distribution (z-score) of the DM regions identified to be driving the separation between age groups.
Figure 2.
(A) Differentially methylated (DM) regions between one- (S+1) and three-year old fish (S+3). Numbers indicate DM regions (based on One-way ANOVA P<0.05 or FDR-adjusted P < 0.05, in brackets). (B) Scores plot of partial least-squares discriminant analysis (PLS-DA) of muscular methylated regions from S+1 and S+3 animals. MBD-seq data were the normalized values of differentially methylated 25-bp genomic regions (One-way ANOVA, P < 0.05). (C) Heatmap showing the abundance distribution (z-score) of the DM regions identified to be driving the separation between age groups.
Figure 3.
(A) Numbers of discriminant DE transcripts, discriminant DM transcripts (containing DM regions), and the overlapping discriminant DE transcripts with DM regions. Bar plots depicting the results of an over-representation test performed over the GO-BP terms of the discriminant DE transcripts (B) and of the overlapping discriminant DE transcripts with DM regions (C). * indicates that the supra-category appears in C. Met., metabolic; Cel., cellular; Reg., regulation; Multicel., multicellular.
Figure 3.
(A) Numbers of discriminant DE transcripts, discriminant DM transcripts (containing DM regions), and the overlapping discriminant DE transcripts with DM regions. Bar plots depicting the results of an over-representation test performed over the GO-BP terms of the discriminant DE transcripts (B) and of the overlapping discriminant DE transcripts with DM regions (C). * indicates that the supra-category appears in C. Met., metabolic; Cel., cellular; Reg., regulation; Multicel., multicellular.
Figure 4.
Correlation analysis between differentially methylation and differential expression (both as log2 fold change in rpkm values between S+3 and S+1 fish) of the overlapping transcripts showing an opposite effect of DNA methylation and expression (A) and of the down-regulated overlapping transcripts associated to hypo-methylated CpGs (B). (C) Bar plot representing the numbers of selected genes showing an opposite trend for DNA methylation and expression (hyper-methylated + down-regulated and hypo-methylated + up-regulated).
Figure 4.
Correlation analysis between differentially methylation and differential expression (both as log2 fold change in rpkm values between S+3 and S+1 fish) of the overlapping transcripts showing an opposite effect of DNA methylation and expression (A) and of the down-regulated overlapping transcripts associated to hypo-methylated CpGs (B). (C) Bar plot representing the numbers of selected genes showing an opposite trend for DNA methylation and expression (hyper-methylated + down-regulated and hypo-methylated + up-regulated).
Figure 5.
Chart representing the filters and criteria applied for matching wide-transcriptomics (RNA-seq) and wide-genomic DNA methylation (MBD-seq) approaches in order to record candidate markers of biological age in gilthead sea bream.
Figure 5.
Chart representing the filters and criteria applied for matching wide-transcriptomics (RNA-seq) and wide-genomic DNA methylation (MBD-seq) approaches in order to record candidate markers of biological age in gilthead sea bream.
Figure 6.
Flow chart representing the multiomic layer integration and the different bionformatic analysis and filters applied after wide-transcriptomics (RNA-seq) and wide-genomic DNA methylation (MBD-seq) approaches in order to obtain a list of candidate markers of biological age in gilthead sea bream.
Figure 6.
Flow chart representing the multiomic layer integration and the different bionformatic analysis and filters applied after wide-transcriptomics (RNA-seq) and wide-genomic DNA methylation (MBD-seq) approaches in order to obtain a list of candidate markers of biological age in gilthead sea bream.
Table 1.
Functional processes (GO-BP ancestors) associated to the selected genes with opposite effect of DNA methylation and expression (33), ordered by the number of selected linked genes (n). The name of these genes and the corresponding age-related changes in DNA methylation and expression are also presented (genes in green, hyper-methylated and down-regulated; gene in red, hypo-methylated and up-regulated). Met., metabolic; Cel., cellular; Reg., regulation; Multicel., multicellular.
Table 1.
Functional processes (GO-BP ancestors) associated to the selected genes with opposite effect of DNA methylation and expression (33), ordered by the number of selected linked genes (n). The name of these genes and the corresponding age-related changes in DNA methylation and expression are also presented (genes in green, hyper-methylated and down-regulated; gene in red, hypo-methylated and up-regulated). Met., metabolic; Cel., cellular; Reg., regulation; Multicel., multicellular.
Functional process |
n |
Genes |
System development |
17 |
abi3bp, arhgap24, bmp1, calcrl, col5a1, kcp, mical2, myo18b, nrp2, spred2, thrb, wfikkn2, parp3, psmd2, ramp1, sirt1, smad1 |
Anatomical structure development |
12 |
arhgap24, calcrl, col5a1, kidins220, mical2, myo18b, nrp2, thrb, phf6, ramp1, sirt1, smad1 |
Anatomical structure morphogenesis |
12 |
arhgap24, bmp1, calcrl, col5a1, mical2, myo18b, nrp2, thrb, psmd2, ramp1, sirt1, smad1 |
Reg. multicel. organismal process |
11 |
abi3bp, atp1a2, bmp1, calcrl, sema6d, spred2, zbtb20, parp3, scn3b, sirt1, smad1 |
Cel. component organization |
10 |
abi3bp, bmp1, col5a1, col6a3, colgalt1, kirrel1, mical2, nrp2, olfml2a, myoz2 |
Response to endogenous stimulus |
10 |
atp1a2, kcp, kidins220, nrp2, spred2, thrb, wfikkn2, ramp1, sirt1, smad1 |
Animal organ development |
9 |
abi3bp, bmp1, calcrl, col5a1, mical2, nrp2, spred2, thrb, smad1 |
Reg. cel. process |
9 |
abi3bp, calcrl, col5a1, colgalt, ksr1, nrp2, ramp1, sirt1, smad1 |
Anatomical structure formation |
8 |
arhgap24, calcrl, col5a1, nrp2, myoz2, ramp1, sirt1, smad1 |
Reg. developmental process |
8 |
abi3bp, bmp1, col5a1, sema6d, spred2, psmd2, sirt1, smad1 |
Reg. localization |
4 |
atp1a2, fgf14, hecw2, scn3b |
Tissue development |
4 |
bmp1, col5a1, sirt1, smad1 |
Transport |
4 |
atp1a2, fgf14, hecw2, scn3b |
Response to chemical |
3 |
calcrl, zbtb20, sirt1 |
N compound met. process |
2 |
psmd2, srm |
Ossification |
2 |
bmp1, smad1 |
Rhythmic process |
2 |
tef, sirt1 |
Cell differentiation |
1 |
col5a1 |
Table 2.
Selected genes with opposite effect of DNA methylation and expression (33) ordered by the number of functional processes (GO-BP ancestors; n) they are involved (genes in green, hyper-methylated and down-regulated; gene in red, hypo-methylated and up-regulated; genes in bold, containing methylated CpG in a regulating area). The names of the corresponding functional processes are also presented. Met., metabolic; Cel., cellular; Reg., regulation; Multicel., multicellular.
Table 2.
Selected genes with opposite effect of DNA methylation and expression (33) ordered by the number of functional processes (GO-BP ancestors; n) they are involved (genes in green, hyper-methylated and down-regulated; gene in red, hypo-methylated and up-regulated; genes in bold, containing methylated CpG in a regulating area). The names of the corresponding functional processes are also presented. Met., metabolic; Cel., cellular; Reg., regulation; Multicel., multicellular.
Genes |
n |
Functional processes |
sirt1 |
11 |
Anatomical structure development, Anatomical structure formation, Anatomical structure morphogenesis, Reg. cel. process, Reg. developmental process, Reg. multicel. organismal process, Response to chemical, Response to endogenous stimulus, Rhythmic process, System development, Tissue development |
smad1 |
11 |
Anatomical structure development, Anatomical structure formation, Anatomical structure morphogenesis, Animal organ development, Ossification, Reg. cel. process, Reg. developmental process, Reg. multicel. organismal process, Response to endogenous stimulus, System development, Tissue development |
col5a1 |
10 |
Anatomical structure development, Anatomical structure formation, Anatomical structure morphogenesis, Animal organ development, Cell differentiation, Cel. component organization, Reg. cel. process, Reg. developmental process, System development, Tissue development |
calcrl |
8 |
Anatomical structure development, Anatomical structure formation, Anatomical structure morphogenesis, Animal organ development, Reg. cel. process, Reg. multicel. organismal process, Response to chemical, System development |
nrp2 |
8 |
Anatomical structure development, Anatomical structure formation, Anatomical structure morphogenesis, Animal organ development, Cel. component organization, Reg. cel. process, Response to endogenous stimulus, System development |
bmp1 |
8 |
Anatomical structure morphogenesis, Animal organ development, Cel. Component organization, Ossification, Reg. developmental process, Reg. multicel. Organismal process, System development, Tissue development |
ramp1 |
6 |
Anatomical structure development, Anatomical structure formation, Anatomical structure morphogenesis, Reg. cel. process, Response to endogenous stimulus, System development |
abi3bp |
6 |
Animal organ development, Cel. component organization, Reg. cel. process, Reg. developmental process, Reg. multicel. organismal process, System development |
mical2 |
5 |
Anatomical structure development, Anatomical structure morphogenesis, Animal organ development, Cel. component organization, System development |
Thrb |
5 |
Anatomical structure development, Anatomical structure morphogenesis, Animal organ development, Response to endogenous stimulus, System development |
spred2 |
5 |
Animal organ development, Reg. developmental process, Reg. multicel. organismal process, Response to endogenous stimulus, System development |
arhgap24 |
4 |
Anatomical structure development, Anatomical structure formation, Anatomical structure morphogenesis, System development |
psmd2 |
4 |
Anatomical structure morphogenesis, N compound met. process, Reg. developmental process, System development |
atp1a2 |
4 |
Reg. localization, Reg. multicel. organismal process, Response to endogenous stimulus, Transport |