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First published online July 20, 2006
Journal of Experimental Biology 209, 2893-2901 (2006)
Published by The Company of Biologists 2006
doi: 10.1242/jeb.02320
Effects of hypo- and hyperoxia on transcription levels of five stress genes and the glutathione system in liver of Atlantic cod Gadus morhua
1 National Institute of Nutrition and Seafood Research, N-5817 Bergen,
Norway
2 Norwegian Institute for Water Research, N-0411 Oslo, Norway
3 Department of Ecology and Natural Resource Management, Norwegian
University of Life Sciences, N-1432 Aas, Norway
4 Fiskeriforskning, N-9291 Tromsø, Norway
* Author for correspondence (e-mail: pal.olsvik{at}nifes.no)
Accepted 10 May 2006
| Summary |
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Key words: Atlantic cod, hyperoxia, hypoxia, oxidative stress, gene expression, oxidative stress index, glutathione
| Introduction |
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In fish, exposure to hyperoxia can induce a reduction in gill ventilation
and elevate the partial pressure of CO2 in the blood, resulting in
a respiratory acidosis and chloremia
(Heisler, 1993
). The
respiratory acidosis may be compensated within days, but short-term exposure
to hyperoxia may cause gill oxidative cell damage
(Brauner et al., 2000
).
Long-term effects of exposure to hyperoxia are less known, but reducing
PO2 is the simplest and most efficient way to limit
production of reactive oxygen species (ROS)
(Massabuau, 2001
). Directly or
indirectly PO2-induced stress is likely to be seen in all
metabolically active tissues including liver cells, as the liver is one of the
most important detoxifying organs in fishes
(Di Giulio et al., 1995
).
Oxygen is a known limiting factor for fish metabolism, and exposure to hypoxia
may lead to reduced growth and activity
(Brett, 1979
).
The Atlantic cod (Gadus morhua) has a wide distribution across the
continental shelf regions of the North Atlantic. Several important cod stocks
are of great economic and social importance. However, many stocks have
suffered from extreme fishing pressure in recent years, and several of them
are showing clear signs of overexploitation
(Hannesson, 1996
).
Considerable efforts have therefore been put into establishing cod
aquaculture, and oxygenation of the rearing water is a probable strategy to
boost production also for this marine coldwater species. In its natural
habitat, Atlantic cod will rarely experience oxygen-free conditions, but
reduced ambient oxygenation is encountered both locally in deep areas of
fjords, as well as larger areas in the Baltic Sea
(Tomkiewicz et al., 1997
) and
Gulf of St Lawrence (D'Amours,
1993
). It has been shown that Atlantic cod is relatively tolerant
to hypoxia (Claireaux and Dutil,
1992
; Scholtz and Waller,
1992
; Schurmann and
Steffensen, 1992
) and survive oxygen saturation levels well below
50% for short periods, i.e. 96 h (Plante
et al., 1998
), Reduced oxygen levels have a strong impact on
aerobic metabolic scope (Claireaux et al.,
2000
), and results in reduced food consumption and growth
(Chabot and Dutil, 1999
).
Since most marine fish species seldom experience hyperoxia in their natural
habitats, little is known about effects of high O2 saturation in
temperate marine environments.
A number of techniques have been used to study oxidative stress in animal
cells, caused either by excessive production of ROS or reduced antioxidant
defence (Armstrong, 2002
). Many
markers have been developed for evaluating the perturbations in cell function
resulting from increased oxidative stress
(Halliwell and Gutteridge,
1999
). Among the most studied are the antioxidant defence enzymes
Cu/Zn superoxide dismutase (SOD), catalase and phospholipid hydroperoxide
glutathione peroxidase (GSH-Px). Cu/Zn SOD is a metalloenzyme that catalyze
the dismutation of superoxide anion (O -2) into
O2 and hydrogen peroxide (H2O2) in the
cytosol, mitochondria and nucleus
(Fridovich, 1986
).
Subsequently, H2O2 is reduced to H2O by
GSH-Px in the cytosol, or by catalase in the peroxisomes or in the cytosol.
Cu/Zn SOD, catalase and GSH-Px, together with glutathione S-transferase and
glutathione reductase, are easily induced by oxidative stress, and the
activity levels of these enzymes have been used to quantify oxidative stress
in cells (van der Oost et al.,
2003
). Both metallothionein (MT) and cytochrome P450 1A (CYP1A)
are considered as general stress proteins, and their transcription have been
shown to be affected by oxidative stress
(Andrews, 2000
;
Morel and Barouki, 1999
). MT
is an efficient scavenger of the hydroxyl radicals (OH-), and yeast
and mammalian MTs can functionally substitute for SOD in protecting yeast from
oxidative stress (Andrews,
2000
). Glutathione (GSH) and GSH disulfide (GSSG) are biologically
important intracellular thiols, and alterations in the ratio between total
glutathione (tGSH) and GSSG (oxidative stress index) are also often used to
assess exposure of cells to oxidative stress.
An increasing number of fish genes are currently being sequenced, allowing
quantification of transcription levels of genes in animals exposed to
environmental challenges. Transcription analysis can be useful supplements to
protein examinations, as the transcriptome represent a snapshot of the cell
activity at a given time. The transcription levels of single genes can be
useful biomarkers of stress in animals
(Bustin, 2002
). However, as
revealed by the increasing use of microarray analysis, altered molecular
expression caused by specific exposures may be very complex, necessitating
careful examination and evaluation in the field of toxicogenomics. Real-time
PCR has recently become the new state-of-the-art methodology for single gene
expression analysis (Bustin,
2004
). The technology offers high throughput, and can combine high
sensitivity with reliable real-time quantification of the target sequence.
As cod is now entering the intensive aquaculture arena, it is necessary to
describe and later define levels of water quality that are within the natural
and tolerable level, to be able to set criteria for `welfare levels'. As a
group, we have been working to define such levels for Atlantic salmon
(Salmo salar) (Olsvik et al.,
2005a
). Turning focus to other species, the aim of this work was
to study oxidative stress in Atlantic cod exposed to suboptimal oxygen
saturation levels. A set of well established markers for oxidative stress in
animals were selected for analysis. These included gene transcripts for three
important antioxidant enzymes (superoxide dismutase, catalase and glutathione
peroxidase), and transcripts for two general stress proteins (metallothionein
and cytochrome P450 1A). Real-time qRT-PCR was used to study the transcript
levels of these genes in hepatic tissue of cod exposed to three levels of
O2 saturation (hypoxia, normoxia and hyperoxia). In addition, the
glutathione status was evaluated in the same liver samples.
| Materials and methods |
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pH, 7.9;
CO2, average 1.8 mg l-1. The specific water flow through
the system was on average 1.52 l kg-1 min-1. A
continuous light exposure regime was used during the experiment, and the cod
were fed ad libitum. The 18 cod sampled for this examination were
taken from a larger experimental setup. Individuals from each oxygenation
group (N=6) were sampled from three separate tanks. Metacain
(Europharma, Norway; 0.08 g l-1 seawater) was used as a sedative
throughout the whole experiment. The fish were killed by a blow to the
head.
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| Tissue sampling |
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Glutathione, glutathione disulphide and oxidative stress index
Livers were thawed, homogenized on ice, and centrifuged (10 000
g, 15 min, 4°C). The resulting supernatant was divided
into two separate tubes and subjected to analysis of total glutathione (tGSH)
and the oxidized form glutathione disulphide (GSSG). Levels of tGSH and GSSG
were measured by a modified microtitre method originally developed by
Vandeputte et al. (Vandeputte et al.,
1994
). In essence, tGSH was determined by adding 20 µl of
blanks, diluted samples or standards and 200 µl of an EDTA buffer (143 mmol
l-1 phosphate buffer, 6.3 mmol l-1 EDTA (Merck KGaA,
Darmstadt, Germany; pH 7.5) containing 0.8 mmol l-1
5.5'-dithiobis (2-nitrobenzoic acid) (DTNB, Sigma-Aldrich), 0.27 mmol
l-1 reduced ß-nicotinamide adenine dinucleotide phosphate
(ß-NADPH, Sigma-Aldrich) to each microtitre well. After 5 min
equilibration, 40 µl EDTA buffer containing 17 i.u. ml-1
glutathione reductase (GR; Sigma-Aldrich) was added and the reduction of DTNB
was monitored at 405 nm for 2 min (kinetic endpoint).
Glutathione disulphide (GSSG) was determined after a 60 min derivatisation of GSH by 20 µl ml-1 vinylpyridine (VP; Sigma-Aldrich), and neutralization by 30 µl ml l-1 triethanolamine (TEA; Merck KGaA). Following derivatisation, 20 µl of blank, sample or standard was added to 200 µl of EDTA buffer containing 0.08 mmol l-1 DTNB and 0.27 mmol l-1 ß-NADPH in each microtitre well. After 5 min equilibration, 40 µl GR in EDTA buffer (1.7 i.u. ml-1) was added and the reduction of DTNB was monitored at 405 nm.
Reduced and oxidized glutathione was determined from a standard curve of GSH and GSSG, respectively. Protein levels in supernatant were determined by the Lowry method using porcine gamma-globulin (Bio-Rad) as the protein standard. Oxidative stress index (OSI) was calculated as the ratio between GSSG and tGSH [OSI=100x(2xGSSG/tGSH)].
RNA extraction
Total RNA was extracted using Trizol reagent (Invitrogen, Life
Technologies), according to the manufacturer's instructions and stored in 100
µl RNase-free MilliQ H2O. Genomic DNA was eliminated from the
samples by DNase treatment according to the manufacturer's instructions
(Ambion, Austin, TX, USA). The RNA was then stored at -80°C before further
processing. The quality of the RNA was assessed with the NanoDrop® ND-1000
UV-Vis Spectrophotometer (NanoDrop Technologies, Wilmington, DE, USA) and the
Agilent 2100 Bioanalyzer (Agilent Technologies, Palo Alto, CA, USA). A 260/280
nm absorbance ratio of 1.8-2.0 indicates a pure RNA sample. The RNA 6000 Nano
LabChip® kit (Agilent Technologies, Palo Alto, CA, USA) was used to
evaluate the integrity of the RNA.
Design of PCR primers
PCR primers used for quantification of the genes encoding Cu/Zn superoxide
dismutase (SOD), phospholipid hydroperoxide glutathione peroxidase (GSH-Px),
metallothionein (MT), elongation factor 1A (EF1A) and ß-actin were
designed using the Primer Express 2.0 software (Applied Biosystems, Foster
City, CA, USA). The RNA sequences of SOD and GSH-Px were obtained from GenBank
accession numbers: CO541611, CO542193, CO542775, CO541820 and CO541508. For
catalase and CYP1A, we designed primer pairs in conserved regions of these
genes based on comparison with other fish species, and amplified DNA products
of about 600 base pairs in Atlantic cod. These DNA products were sequenced and
used to design PCR primers for amplification of catalase and CYP1A in Atlantic
cod. The sequences have been uploaded to the GenBank (acc. nos. DQ270487,
DQ270488). The PCR primers for SOD, GSH-Px, MT, EF1A and ß-actin were not
designed to span exon-exon borders, as they were made from mRNA sequences.
Instead, the extracted RNA samples were subjected to DNA-free treatment to
avoid genomic DNA contamination, and amplified PCR products of all five genes
were sequenced and BLASTed to ensure that the correct mRNA sequences were
quantified. Primer sequences are given in
Table 2. The genes were
sequenced with the BigDye version 3.1 sequencing kit (Applied Biosystems,
Foster City, CA, USA), using an ABI PRISM® 377 DNA Sequencer at the
University of Bergen Sequencing Facility. For assay verification, a one-step
RT-PCR protocol was used to amplify the genes (Qiagen OneStep RT-PCR kit)
(Qiagen, Chatsworth, CA, USA). The PCR products were run on a 2% agarose gel,
and subsequently sequenced as described above.
|
Real-time quantitative RT-PCR
A semi-quantitative two-step real-time RT-PCR protocol was developed to
measure the transcript levels of Cu/Zn SOD, catalase, GSH-Px, MT, CYP1A, EF1A
and ß-actin in liver cells of Atlantic cod. Twofold serial dilution
curves of total RNA were used for RT and PCR efficiencies calculations. The
five serial dilutions and all samples for each gene were run on the same
96-well plate. The RT reactions were run in triplicates on 96-well reaction
plates with the GeneAmp PCR 9700 machine from PE Applied Biosystems with the
TaqMan Reverse Transcription Reagent containing Multiscribe Reverse
Transcriptase (50 i.u. µl-1; all chemicals mentioned in this and
the next paragraphs were from Applied Biosystems). Reverse transcription was
performed at 48°C for 60 min using oligo(dT) primers (2.5 µmol
l-1) for the studied genes in 30 µl total volume. Input RNA
concentration was 250 ng in each reaction. The final concentrations of the
other chemicals in each RT reaction were as follows: MgCl2 (5.5
µmol l-1), dNTP (500 µmol l-1 of each), 10x
TaqMan RT buffer (1x), RNase inhibitor (0.4 i.u. µl-1) and
Multiscribe Reverse Transcriptase (1.67 i.u. µl-1).
0.5 µl of cDNA from each RT reaction was transferred to a new 96-well
reaction plate, and the real-time PCR run on the ABI Prism 7000 Sequence
Detection System from Applied Biosystems (Applied Biosystems, Foster City, CA,
USA). Real-time PCR was performed by using QuantiTect SYBR Green PCR Master
Mix (Qiagen, Chatsworth, CA, USA), according to the manufacturer's
instructions. Baseline and threshold for Ct calculation were set manually with
the ABI Prism 7000 SDS software version 1.0, (Applied Biosystems, Foster City,
CA, USA) and mean normalized expression was calculated with the Microsoft
Excel-based software Q-Gene. The Q-Gene tool was developed to manage and
expedite the entire experimental process of quantitative real-time RT-PCR, and
is offered at no cost from the BioTechniques Software Library
(Muller et al., 2002
). EF1A
was used as an endogenous control in the final calculations of mean normalized
expression, as this gene was slightly more stable than ß-actin, assessed
by the geNorm Microsoft Excel-based tool for the determination of the most
stable housekeeping genes (Vandesompele et
al., 2002
).
|
| Results |
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Glutathione, glutathione disulphide and oxidative stress index
No significant differences were found for hepatic concentrations of total
glutathione (tGSH) (control value 46.5±15.0 nmol mg-1),
glutathione (GSH; control value 44.6±14.4 nmol mg-1),
glutathione disulphide (GSSG; control value 1.8±0.8 nmol
mg-1) and oxidative stress index (OSI; control value
7.4±1.5%) between the groups of cod kept in various oxygen saturation
levels (Kruskal-Wallis test, values given as mean ± s.d.; data not
shown). Overall, the glutathione system in liver tissue of cod seems
unaffected by exposure to hypoxia and hyperoxia for long periods, such as 6
weeks.
|
The 6-week exposure experiment revealed significant differences in transcript levels of the antioxidant genes of SOD and GSH-Px in liver of Atlantic cod exposed to three different saturation levels of O2 over a prolonged period of time (Kruskal-Wallis test) (Fig. 2). No subgroup differences were found for SOD (Dunn's multiple comparison posttest), but the overall Kruskal-Wallis test gave a significant results (P=0.0416). For GSH-Px, the transcript level was significantly downregulated in the hypoxia group compared to both the control group (P<0.05) and the hyperoxia group (P<0.01). The overall Kruskal-Wallis test for GSH-Px gave a significant result (P=0.0023). Compared to the control group, there was also a trend towards upregulation in the hyperoxia group for SOD and GSH-Px. No effects were found for the transcript levels of catalase, the third antioxidant examined. The transcript levels of MT did not change in liver as a result of exposure to hypoxic or hyperoxic conditions. Individual variation of MT transcription was large in all three groups, with coefficients of variation (CV) ranging in the order from 43-79%. CYP1A transcription was significantly downregulated in the hypoxia group compared to hyperoxia group (P<0.05), with a overall Kruskal-Wallis test value for this gene of P=0.00203. The standard deviation of the hyperoxia group was much greater than in the hypoxia and normoxia groups, indicating that exposure to high O2 saturation levels may trigger an upregulation of CYP1A in liver tissue of cod.
For biomarker assessment, Spearman rank correlation analysis was performed between individual SGR and OSI values and the transcription levels of SOD, catalase, GSH-Px, MT and CYP1A. Significant correlations were found between individual SGR and SOD transcription (P=0.0139, r=0.58) and SGR and GSH-Px transcription (P<0.0004, r=0.76), but not between SGR and catalase transcription. No significant correlation was found between SGR and MT transcription, whereas the correlation between SGR and CYP1A was significant (P=0.0225, r=0.55). Based on individual values, no significant correlations were found between the OSI and the other quantified parameters (Spearman rank correlation).
|
| Discussion |
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Glutathione, glutathione disulphide and oxidative stress index
The tripeptide glutathione (GSH) is synthesized by specific enzymes and is
present intracellularly in high concentrations. Under homeostasis, more than
90% of GSH is present in reduced form
(Halliwell and Gutteridge,
1999
). GSH is an important reductant, involved in removal of
H2O2 (directly or indirectly) by GSH-Px in the cytosol,
stabilization of the redox state of peptides and proteins by the
protein-disulfide reductase reaction, or conjugation reactions for
neutralizing xenobiotics and biosynthesis. In liver cells, a substantial
portion of the intracellularly synthesized GSH may be exported out of the
cells. GSSG, the oxidized form of glutathione, resulting from these reactions,
is reduced again in a NADPH-dependent reaction by glutathione reductase.
Regulation of the GSH system is essential for the cells. In general, cellular
GSH is increased in times of stress, and downregulated after an oxidative
assault has been overcome (Halliwell and
Gutteridge, 1999
). The glutathione status is therefore critically
important for the defence against oxidative stress in fish.
The oxidative stress index (OSI) in liver of cod exposed to low or high
O2 concentrations were not significantly different from the
normoxia fish. Also no significant differences were seen between the three
examined groups for the concentrations of tGSH, GSSG or GSH in liver tissue.
The ratio of reduced GSH to total GSH was very stable in all levels of
exposure (0.960±0.009), suggesting that sufficient GSH is maintained in
its reduced form to protect the cells. GSH turnover is low under normal
conditions and GSH levels remain unchanged in channel catfish for several days
if synthesis is inhibited (Gallagher et
al., 1992
). In human hepatocytes it has been shown that as long as
the GSH-Px-GSH reductase system is unaffected, even relatively low amounts of
GSH can protect the cells by supporting glutathione peroxidase-mediated
metabolism of H2O2 and lipid hydroperoxides
(Eklow-Lastbom et al., 1986
).
A large number of factors are known to affect intracellular GSH levels, i.e.
toxicant exposure, nutritional status, temperature etc. Imbalance of
intracellular GSH can affect the fish's ability to respond to stress
(Leggatt and Iwama, 2003
). Our
data suggest that Atlantic cod are able to maintain stable glutathione redox
capacity under moderately hyperoxic and hypoxic conditions, which affect gross
anatomical features such as specific growth rate. However, whether the
apparent homeostasis in glutathione redox capacity was due to low sensitivity
of the glutathione system for hypoxia and hyperoxia, or whether the stable
concentrations are due to a compensatory regulation, remains to be clarified.
The vitamin E supplemented diet used in the current experiment might have
contributed to the unaffected levels of GSH, since this strong antioxidant can
increase the levels of GSH in liver of fish fed vitamin E rich diets
(Hamre et al., 1997
). This may
be due to an indirect coupling of GSH to vitamin E recycling by its ability to
regenerate ascorbic acid (Packer and
Kagan, 1993
). As we only have data from the end of the
experimental period, we cannot exclude that the groups of animals exposed to
high and low oxygen levels have gone through variations in activity in the
parameters we have analyzed. Despite not having data from the start of the
experiment, we assume the different experimental groups of animals were
comparable, as they were randomly selected from larger populations.
Gene expression
It is well known that sub-optimal oxygen saturation levels may induce
health problems in fish in modern aquaculture
(Wedemeyer, 1997
). Gene
expression analysis has the potential to precede early signs of injury and be
predictive of adverse events. The number of known gene sequences has recently
increased rapidly in many fish species, enabling scientists to look for novel
biomarkers based on gene expression studies. Real-time qRT-PCR has in recent
years been transformed from an experimental tool to a mainstream scientific
technique (Bustin, 2004
). Even
though different RT-PCR protocols may be reasonably straightforward
technically, and yield reproducible results, the expression data
interpretation is still a challenge, especially in relation to traditional
markers. Messenger RNAs are in general shortlived, and in eukaryotes most mRNA
is degraded within a few hours after synthesis
(Fan et al., 2002
). The rapid
mRNA turnover means that external or internal stimuli can rapidly change the
rate of synthesis of individual mRNA and thereby alter the composition of the
transcriptome within hours.
In the current study, the transcript levels of both SOD and GSH-Px were
significantly downregulated in individuals exposed to hypoxia compared to
individuals kept under normoxia conditions. There may be at least three
possible explanations for this finding. First, even with the semi-chronic
nature of the current experiment, oxidative stress was lower in animals
exposed to hypoxia, resulting in lower transcript levels of these genes. This
may be the result of suppressed tissue activity with reduced cell turnover and
proliferation of liver cells. Second, hypoxia may act as a corepressor of
transcription activity (see Lemon and
Tjian, 2000
) in liver cells of fish exposed to low oxygen
saturation levels. Two of the most significant hypoxia defence mechanisms
found in the animal kingdom include (i) severe downregulation of energetic
efficiency and (ii) upregulation of the energetic efficiency of ATP-producing
pathways (Hochachka and Lutz,
2001
). Since ATP is the energy source of the transport mechanisms
responsible for the transmembrane transport of ions, and this transport is the
single largest ATP consumer in cells, channel arrest may explain the
downregulation of these central antioxidant genes in the hypoxia-exposed fish.
Third, tissue sampling for transcription analysis included several cell types,
potentially masking transcriptional differences in the studied genes. In
addition to hepatocytes, liver tissue also contain other cell types such as
Kupffer cells, stellate cells, endothelian cells, bile conduct cells and
varying amounts of infiltrating blood cells
(Akiyoshi and Inoue, 2004
). The
heterogeneous nature of liver tissue may therefore dilute gene expression
events as quantified by real-time RT-PCR on tissue samples.
At the same time, GSH-Px was significantly upregulated in the hyperoxia
group, indicating increased oxidative stress in this group. Exposure to
hyperoxia can cause generation of ROS and thereby increased oxidative stress
in animals (Parinandi et al.,
2003
; Buccellato et al.,
2004
). Few examinations have been conducted on the regulation of
antioxidant enzyme gene transcription in fish exposed to hyperoxia
(Nikinmaa and Rees, 2005
).
From an examination of the transcript levels of SOD, GSH-Px and catalase, in a
recent study in Atlantic salmon Salmo salar
(Olsvik et al., 2005a
), we
were not able to conclude that exposure to 130% oxygen saturation caused
oxidative stress. However, other studies on salmonids
(Lygren et al., 2000
;
Ritola et al., 2002
) have
revealed that fish may be vulnerable to ROS-generated oxidative stress after
hyperoxia exposure, based on reduced activities of antioxidant enzymes and
antioxidant vitamins and increased thiobarbituric acid-reactive substances
(TBARS). Additional knowledge on how inadequate oxygenation levels affect
biological systems might be gained by simultaneously monitoring gene
transcription and expression, and activities of antioxidant proteins. These
parameters should, if possible, be measured together in future examinations to
give more relevant biological information, i.e. on post-transcriptional
regulation of antioxidant enzyme gene expression.
Although MT and CYP1A act differently under many forms of environmental
stress, both proteins have been considered as prime biomarkers of oxidative
stress exposure in aquatic animals (Bucheli
and Fent, 1995
; Viarengo et
al., 2000
). In mammals, hypoxia is known to activate MT gene
expression through metal responsive elements
(Murphy et al., 1999
). In the
current study, the transcript levels of MT in the liver of the fish did not
change in response to altered oxygen saturation in the water. Induction of
cytochrome P4501A (CYP1A) is certainly one of the best studied biomarkers in
fishes. Human CYP1A1 is downregulated at the transcriptional level by
oxidative stress, depending on the nuclear factor 1 site located on the
proximal promoter of the gene (Morel and
Barouki, 1999
). In the current study, CYP1A was significantly
downregulated in the hypoxia group, but not altered in the hyperoxia group
compared to the normoxia group (although the covariance increased in the
hyperoxia group). In general, hypoxia is expected to lead to decreased ROS
production, but may also lead to increased oxidative stress. The molecular
mechanisms involved in the downregulation of CYP1A transcription in liver of
hypoxia-exposed cod are unknown.
Biomarker evaluation
Among fishes there is a wide range of oxygen tolerance. Cold-adapted marine
fish species normally needs high oxygen levels, in contrast to, for example,
hypoxia-tolerant cyprinid species
(Lushchak et al., 2001
).
Plante et al. (Plante et al.,
1998
) showed that the Atlantic cod can survive for shorter periods
at surprisingly low oxygen saturation levels, with a 96 h LC50
value of 26% O2 at 6°C. The range of published values of
hypoxic lethal thresholds for this species is 5-40% O2 saturation.
Physiological parameters measured after 96 h of exposure indicated only weak
responses to low oxygen. Even if a number of physiological processes are known
to be altered by hypoxia in fish (Nikinmaa
and Rees, 2005
), the hypoxia stress imposed in this work was
therefore expected to only have moderate effects on the physiological status
of the fish. In hypoxia the effectiveness of O2 uptake is reduced,
and in many fish species O2 consumption increases as
PO2 drops (Nilsson and
Renshaw, 2004
). Adaptation to low oxygen saturation may involve
metabolic rate depression, rearrangement of blood flow to mainly brain and
heart and increased efficiency of energy production. Protein synthesis may
also be downregulated during hypoxia in organs such as muscle and liver, as
shown in crucian carp (Smith et al.,
1999
). Buck and Hochachka
(Buck and Hochachka, 1993
)
found that ATP demands for protein synthesis in hepatocytes in the
anoxia-tolerant turtle Chrysemys dropped from 55% of the total ATP
consumption to approximately 10% within minutes of exposure to anoxia.
Both hypoxia and hyperoxia may result in physiological adaptations that are
not reflected by the transcriptome after 6 weeks of exposure, although earlier
studies have shown decreased SOD and GSH-Px enzyme activities in
hyperoxygenated Atlantic salmon after exposure to 140-150% oxygen saturation
for 6 weeks (Lygren et al.,
2000
). The suitability of SOD, catalase and GSH-Px transcription
as biomarkers of hyperoxia-induced oxidative stress in fish may therefore be
limited. However, the standing antioxidant defence, GSH and antioxidant
vitamins etc., is an integrated and very complex system, involving feedback
mechanisms and signalling systems
(Halliwell and Gutteridge,
1999
; Benzie, 2003
;
Ghezzi, 2005
). Importantly,
the gene transcription snapshot at a given time might not represent the
exposure experiment. For example, endogenous sources of oxyradical production
might be bigger than exogenous sources due to control imposed by the
diversification of co-activators or corepressor effects
(Lemon and Tjian, 2000
), which
might affect endogenous ROS production and thus camouflage eventual effects of
the hyperoxia exposure. Both oxidants and antioxidants are known to activate
numerous genes and pathways, suggesting that ROS may serve as sub-cellular
messengers in redox-sensitive gene regulatory and signal transduction pathways
(Allen and Tresini, 2000
).
It has been suggested (Depledge,
1994
) that biomarker responses should be related to a given degree
of impairment of growth (SGR), reproductive output, or energy utilization that
directly affects the survivorship and fertility of organisms. Changes at the
biochemical level, however, offer distinct advantages as biomarkers, since
molecular alterations are normally the first detectable, quantifiable
responses to environmental changes, and may therefore serve as markers of both
exposure and effect (Huggett et al.,
1992
). Our data suggest that the transcriptional levels of GSH-Px
might be a useful biomarker for both hypoxia and hyperoxia stress in liver of
Atlantic cod, as this parameter was strongly correlated to SGR in the studied
fish. Similar positive correlations were found between SGR and the
transcriptional levels of SOD and CYP1A. No significant correlations were
found between SGR and the transcriptional levels of catalase and MT. Neither
did we find any significant correlations between the OSI and the other
measured parameters. The current research also indicates that the OSI may be
an unsuitable biomarker for hypoxia and hyperoxia exposure in Atlantic cod
liver, since the fish maintains the glutathione system unaltered even under
stress that has great impact on growth as a compensatory response.
In conclusion, we found significantly decreased transcription of SOD, GSH-Px and CYP1A in liver of Atlantic cod after 6 weeks of exposure to 45% oxygen saturation as compared to normoxia fish kept at 76% oxygen saturation. GSH-Px was significantly upregulated in fish exposed to 145% oxygen saturation. Prolonged exposure to unfavourable oxygen saturation levels did not alter the OSI, indicating that the antioxidant glutathione system is maintained at an unchanged level in liver of the examined cod.
| Acknowledgments |
|---|
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|---|
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Allen, R. G. and Tresini, M. (2000). Oxidative stress and gene regulation. Free Radic. Biol. Med. 28,463 -499.[CrossRef][Medline]
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