Abstract
Reactive oxygen species have a great impact on spermatozoa function. Gametes from sole males born in captivity (F1) display lower quality than those from wild individuals. In this paper, the percentage of cells positive for dichlorofluorescein (DCF+) was determined by flow cytometry in wild and F1 animals, the effect of cryopreservation on DCF+ cells was evaluated in both groups and the distribution of H2O2 within the cell was studied by confocal microscopy. Our results indicated that there are no differences in either viability or DCF+ cells between wild and F1 animals when fresh samples were evaluated. However, when data were analyzed considering two different sperm populations in terms of motility, a significant decrease in viability and DCF+ cells was reported in low-motile F1 spermatozoa. Cryopreservation did not alter the viability or the presence of DCF+ cells in sperm samples from wild animals, but significantly decreased the viability in F1 samples. Distribution patterns of H2O2 have been established by confocal microscopy in Solea senegalensis spermatozoa: co-localization of H2O2 with active mitochondria (MitoTracker+) and co-localization with nuclear DNA (DAPI). Compared with H2O2 distribution in other marine species such as Scophthalmus maximus, Solea senegalensis spermatozoa showed widespread presence of H2O2 particularly in the nuclei, which could potentially compromise DNA integrity.
Introduction
Marine aquaculture producers from Southern Europe show an increasing interest in a promising species: Senegalese sole (Solea senegalensis Kaup, 1858). Sole has both a good marketable assessment and very good consumer acceptance. Despite the fact that sole is an appealing candidate for marine aquaculture, this species shows important limitations in industrial culture (Howell et al. 2006, 2009). The absence of courtship in F1 males (Porta et al. 2006) together with poor and variable semen quality, particularly in F1 males, are major obstacles in large-scale production (Cabrita et al. 2006, Martínez-Pastor et al. 2008, Beirão et al. 2009, 2011). This absence of natural reproduction in animals born in captivity makes the use of artificial fertilization methods necessary (Rasines et al. 2013). These methods involve fish manipulation for gamete collection, sperm classification by motility, and cryopreservation for storing the best sperm samples (Sieme et al. 2015) until artificial fertilization trials are performed. Only optimal samples should be used for cryopreservation so as to guarantee good in vitro fertilization results.
Reactive oxygen species (ROS) formation has been recognized as a problem for sperm survival and fertility (Guthrie & Welch 2012). In mammals, oxidative stress damage competence of spermatozoa by peroxidation of lipids, induction of oxidative DNA damage and formation of protein adducts are well known (Aitken et al. 2012). It has also been established that ROS production could initiate an intrinsic apoptotic cascade causing spermatozoa to lose their motility (Aitken et al. 2012). In Senegalese sole, a significantly higher percentage of apoptotic cells in F1 males was reported than those in wild-captured animals (Valcarce et al. 2016). The aim of this work was to investigate the relationship between ROS levels and sperm quality in Solea senegalensis, which presents two particular problems: (1) low sperm quality in F1 samples and (2) the need for sperm to be cryopreserved before artificial fertilization. For this purpose, the intracellular levels of ROS species and viability of sperm samples from wild-captured and F1 males were analyzed by flow cytometry in fresh and cryopreserved samples. Moreover, the distribution of H2O2 in the spermatozoa was studied by confocal microscopy and compared with other marine flat fish species. This analysis gave a molecular insight into sole spermatozoa providing new keys for understanding reproduction failure in Solea senegalensis.
Materials and methods
Ethics
Animal manipulation was carried out following the national and institutional bioethical guidelines and European Union Directive 2010/63/EU for the protection of animals used for experimental and other scientific purposes. The experiments performed in this study are part of project AGL2015 68330C2-1R approved by the IEO ethics committee (1/2016).
Animal maintenance and experimental groups
Wild-captured (WT) and F1 broodstocks (F1) were used in this experiment. Fish labeled as wild-captured males (WT) refers to those born in their natural environment and able to reproduce naturally, whereas those labeled F1 are born in captivity and are unable to reproduce. WT males were captured two years before starting this experiment and, according to their size and weight, were approximately 4 years old. F1 males were 4 years old. Both groups of animals were held indoors at a 1:1 female:male ratio in tanks (4–14 m2 in area and 1 m deep) with a stock density around 5 kg/m3 in the Spanish Institute of Oceanography in Santander (Marine Culture Plant El Bocal). Each tank maintained constant aeration and an open flow circuit (33% tank/h of water renewal). They were exposed to a 16:8 h (light:darkness) continual artificial photoperiod. Light intensity was reduced with mesh shading placed over the tanks. The fish were fed (0.5% of the total biomass) 6 days a week with commercially extruded feed (Vitalis Cal and Vitalis Repro, Skretting). Each animal in the culture plant was monitored with passive integrated transponder tags (PIT tags, AVID) inserted in the dorsal musculature. Three WT (n = 3) and six F1 (n = 6) fish were used for this experiment.
Sperm sample collection
Before collection, the males were anesthetized with 40 ppm clove oil for 2 min. The urogenital pore was always toweled to remove feces, water and mucus before sperm sampling. Contaminated sperm was rejected. Ejaculates were collected with a syringe without a needle by gently pressing the testes on the pigmented side of the fish. The samples were individually maintained at 4°C in microcentrifuge tubes until processing.
Sperm analysis
For each ejaculate (WT: n = 3 and F1: n = 6), cell concentration and volume were analyzed. Percentage of motile spermatozoa was assessed using the scores by Billard and coworkers (1995). For this purpose, 1 μL of prediluted sperm (1:10) in 200 mOsm/kg Ringer solution (116 mM NaCl; 2.9 mM KCl; 1.8 mM CaCl2; 5 mM HEPES, pH 7.7) was activated with 500 μL artificial seawater (24.6 g/L NaCl, 0.67 g/L KCl, 1.36 g/L CaCl2·2 H2O, 6.29 g/L MgSO4·7 H2O, 4.66 g/L MgCl2·6 H2O, 0.18 g/L NaHCO3; 1100 mOsm/kg; pH 8.0) kept at 4°C. Motility was determined under light contrast microscopy (magnification: 200×). This procedure was performed twice for each sperm sample following the method described by Billard (Billard et al. 1995).
Cryopreservation protocol
Each sample was split into two: (1) a fresh aliquot (FRESH) and (2) a cryopreserved aliquot (CRYO). For cryopreservation, cells were diluted (1:2 ratio) in Mounib extender with cryoprotectants (10% BSA and 10% DMSO) following the protocol published by Rasines (Rasines et al. 2013). The samples were loaded into 0.5 mL straws and exposed to liquid nitrogen vapor for 7 min. After this time, the straws were immersed in liquid nitrogen.
Thawing protocol
The samples were thawed in a 40°C bath for 7 s. The cryoprotectants were discarded after centrifugation (1 min; 1000 g) and the cells were resuspended in Ringer solution.
Flow cytometry analysis
Analyses were performed using a NovoCyte Flow Cytometer (Acea Biosciences, San Diego, CA, USA). Viability was measured using propidium iodide (PI) (Sigma), and intracellular sperm ROS levels were studied using dichlorofluorescein diacetate (DCFH-DA) (Sigma), which can precisely reveal intracellular ROS, emitting green fluorescence when oxidized (Fig. 1). Both aliquots (FRESH and CRYO) for each individual (WT and F1) were incubated in 25 µM DCFH-DA (7°C, 40 min) and co-stained with 2 µg/mL PI (Invitrogen) (7°C, 10 min). Overall, 10,000 events were acquired per sample, and the acquisition was performed twice for each sample. Data analysis was performed using NovoExpress software (Acea Biosciences).
As control of the technique for the detection of ROS with DCFH-DA in Solea senegalensis sperm, three samples were split into three: (i) a non-treated aliquot, (ii) an aliquot treated with 100 mM sodium pyruvate (Sigma-Aldrich), a scavenger of reactive oxygen species and (iii) an aliquot treated with 10% H2O2 (Sigma-Aldrich) for 15 min as a positive control. Controls were washed in 1× PBS after treatment and subsequently processed in the usual way.
Measurement of reduced glutathione
To analyze the antioxidant activity in WT and F1 spermatozoa, we studied the intracellular reduced glutathione content for both wild-captured (n = 3) and F1 spermatozoa cryopreserved samples (n = 3). For this purpose, we used a Glutathione Colorimetric Assay Kit (Biovision). In brief, 1 × 106 cells from wild-captured and F1 sperm respectively were used as samples. After lysis and centrifugation, the supernatants were used for the reduced glutathione measurement in a microplate reader as per the manufacturer’s protocol.
Confocal microscopy analysis
To localize the presence of intracellular ROS in Senegalese sole sperm, 1–2 × 106 cells/mL of WT, F1 and controls (15 min; 10 mM sodium pyruvate and 15 min 10% hydrogen peroxide) were incubated with 25 μM DCFH-DA (Sigma) (7°C, 40 min) and 100 nM MitoTracker Deep Red (Invitrogen) (7°C, 10 min). Nuclei were labeled with 4′,6-diamidino-2-phenylindole (DAPI) (Sigma-Aldrich; 1:1000). A 5 μL cell suspension drop was placed on a slide and immediately analyzed under a LSM 800 confocal microscope (Zeiss). To compare the localization of intracellular H2O2 in other flatfish species, confocal microscopy analysis was used following the same protocol described previously with turbot (Scophthalmus maximus) sperm cells.
Statistical methods
Data were analyzed using SPSS, version 20 for Macintosh (SPSS). Data are presented as mean ± s.e.m. in all cases. Mean values of each variable were compared by a one-way ANOVA (P < 0.05). Duncan post hoc test was performed to analyze homogenous subgroups in each parameter.
Results
Sperm viability
Wild-captured vs F1 males
No statistical differences were found between wild-captured (WT-FRESH) and F1 (F1-FRESH) males in fresh samples (Fig. 2 – full colored bars). Good viability (over 60% in both cases) was reported in fresh samples.
Fresh vs cryopreserved samples
Two different patterns were shown: cryopreservation did not significantly decrease viability in wild-captured males (WT-CRYO) (only a reduction of less than 5% of viable cells was recorded) (Fig. 2). On the other hand, males born in captivity (F1-CRYO) were strongly affected by the protocol reporting a statistically significant reduction of around 35%.
F1 generation: high-motility samples vs low-motility samples
To check if the best F1 samples in terms of motility showed a similar tendency to wild male samples, data were reanalyzed in F1 attending to motility. Wild-captured male samples were kept as reference. The F1 group was split into two groups according to their motility (Supplementary Material 1, see section on supplementary data given at the end of this article). Three of them were labeled ‘low-motility samples’ (F1-L MOT; n = 3) with a percentage of motile cells ≤30%, and another three were considered high-motility samples (F1-H MOT; n = 3) with motility values ≥45%). In F1 fresh high-motility samples (Supplementary Material 1A; F1-FRESH-H MOT), viability was similar to sperm samples from wild animals (WT-FRESH), but in low-motility samples (Supplementary Material 1B; F1-FRESH-L MOT), a significant reduction in viability was observed in F1 fresh spermatozoa (54.66 ± 5.41%). After cryopreservation, sperm viability in F1 males decreased in both high- (F1-CRYO-H MOT) and low-motility samples (F1-CRYO-L MOT) (high motility: 56.71 ± 3.94% and low motility: 27.39 ± 2.44%) (Supplementary Material 1A and B – black striped bars).
Sperm ROS level by flow cytometry
The evaluation of intracellular ROS species in Solea senegalensis spermatozoa with DCF by flow cytometry was corroborated by an independent experiment (Supplementary Material 2). Samples treated with sodium pyruvate (scavenger of ROS) presented significantly fewer DCF+ cells, whereas those treated with H2O2 reported higher values than the non-treated sample.
Wild-captured vs F1 males
WT fresh samples (WT-FRESH) presented high levels of DCF+ cells over 50%. There were no statistical differences between this group and F1 fresh samples (F1-FRESH) although a clear tendency of reduction can be seen in the results (Fig. 3 – full colored bars).
Fresh vs cryopreserved samples
No significant differences were found between fresh (WT-FRESH) and cryopreserved samples (WT-CRYO) in wild-captured males, although lower levels of DCF+ cells were found in cryopreserved samples (WT-FRESH: 53.32 ± 4.89% and WT-CRYO: 40.10 ± 5.40) (Fig. 3 – gray bars). The F1 males were not significantly affected by the freezing–thawing process. F1 fresh samples (F1-FRESH) reported 34.76 ± 6.61% DCF+ cells (mean value ± s.e.m.) and cryopreserved spermatozoa showed 21.72 ± 5.81% (mean values ± s.e.m.) (Fig. 3 – black bars).
F1 generation: high-motility samples vs low-motility samples
The previously described split was carried out in this analysis for the F1 generation: high-motility samples (F1-H MOT) vs low-motility samples (F1-L MOT).
High-motility samples reported the same tendency as the global analysis (Supplementary Material 1C and D). Statistical differences were only found between WT-FRESH and F1-CRYO-H MOT samples (Supplementary Material 1C).
F1 low-motility samples (F1-L MOT) presented a different profile (Supplementary Material 1D) compared with high-motility ones. These samples reported a reduction of 66% ROS+ cells compared with WT fresh samples. Following the same tendency, F1 low-motility cryopreserved samples (F1-CRYO-L MOT) showed a reduction of around 84% compared with the WT-CRYO group. No statistical differences were found between fresh and cryopreserved in F1 low-motility samples.
Reduced glutathione levels by colorimetric assay
The colorimetric assay reported a statistically significant higher level of reduced glutathione in F1 samples compared with that in wild-captured ones (Fig. 4).
Cell localization of intracellular H2O2
Confocal microscopy images showed a co-localization of ROS (green fluorescence, DCF labeling) with mitochondria (red fluorescence, MitoTraker labeling) (Fig. 5). The mitochondrial ring is located at the base of the heads of Solea senegalensis spermatozoa, which is observed as intense fluorescent areas in the confocal captures (Fig. 5D). H2O2 is also detected in nuclei (blue, DAPI labeling) showing that oxidative stress is not only present in mitochondria but also could be damaging DNA. This localization pattern was reported in WT and F1 samples (Fig. 5H and I). The intensity of the DCF labeling in the nuclei of Solea senegalensis spermatozoa pointed to a larger presence of ROS species in this compartment of the spermatozoa from Solea senegalensis than in other flat fish such as Scophthalmus maximus (Supplementary Materials 3 and 4).
Discussion
Reactive oxygen species (ROS) have usually been associated to defective sperm function causing cellular damage at different levels. The major source of ROS in spermatozoa is mitochondria. It is well known that oxidative stress produces peroxidation of lipids (Cabrita et al. 2014). It is described that mammalian spermatozoa are particularly vulnerable to this type of damage due to the high amount of polyunsaturated fatty acids (PUFA), which are very vulnerable to free radical attack (Aitken et al. 2012). Lipid peroxidation is very harmful, having a clear negative effect on sperm motility and fertilization (Aitken & Curry 2011). ROS can even trigger an intrinsic apoptotic cascade. It is thought that the only product generated during this cascade capable of producing DNA damage is the H2O2 released from the mitochondria because it is a small chargeless molecule, able to penetrate the nucleus (Aitken et al. 2012). The mechanism by which DNA breakage is caused is by the oxidation of vulnerable bases, particularly guanines, which generates 8-hydroxy, 2-deoxyguanosine (8OHdG). All these events lead to a decrease in motility, viability and DNA integrity and therefore significantly reduce sperm quality (Aitken et al. 2012).
Our study aims to determine the effect the processes such as cryopreservation has on the levels of intracellular H2O2 in Solea senegalensis spermatozoa. Moreover we try to elucidate if the sperm sample’s origin (from wild animals vs animals born in captivity) has an effect on the presence of ROS in these cells. Finally, we studied the distribution of this molecule in the spermatozoa.
To date, studies carried out on oxidative stress of fish could be divided into different types: (1) some reports study the ROS detoxification mechanism (Chauvigné et al. 2015), (2) others study the effect of UV irradiation or other treatments inducing oxidative stress on spermatozoa (Dietrich et al. 2005, Gazo et al. 2015), (3) other approaches evaluate the effect of the addition of antioxidant compounds or the effect of enriched diets (Beirão et al. 2015), (4) others study lipid peroxidation and its relation to decrease in sperm quality (Martínez-Páramo et al. 2012), and finally (5) others evaluate the antioxidant status of seminal plasma and spermatozoa (Shaliutina et al. 2013, Słowińska et al. 2013). Interestingly, in mammals, it has been suggested that seminal plasma could be considered as one of the most powerful antioxidant fluids (Aitken et al. 2012). The common feature of all these types of studies in fish is that ROS are considered deleterious for spermatozoa. From this perspective, our results would indicate that Solea senegalensis spermatozoa have high levels of oxidative stress (DCF+ cells, on average: 53.32 ± 4.89% in WT and 34.76 ± 6.60% in F1) (Fig. 3), and this could make them prone to suffering different types of damage. Surprisingly, the number of DCF+ cells is significantly lower in cryopreserved F1 samples. It is well known that cryopreservation could induce oxidative stress, accelerating ROS production (Thomson et al. 2009, Kim et al. 2010, Aitken et al. 2012). So how can this fact be explained? It is known that the induction of ROS generation by sperm mitochondria is a very early stage within the whole oxidative stress process (Koppers et al. 2008, 2011), which, as expected, happens before DNA damage is produced and cell viability decreases. One possibility is that the oxidative stress process in F1 cryopreserved spermatozoa is in a later stage, so there is much more damage, but levels of ROS are not as high. In fact, when we look at viability results, we observe a significantly lower percentage of viable cells in this group (42.05 ± 5.61%, Fig. 2). In accordance with this hypothesis, when we divided the sperm samples in terms of motility for data analysis, we observed that low-motility samples have a lower percentage of DCF+ cells not only after cryopreservation but also when fresh (Supplementary Material 1). When we look at the viability results, once again a significant decrease in cell viability in F1 fresh low-motility samples is observed. As expected, reduced glutathione levels are also lower in WT cells (with high oxidative stress) than in F1 spermatozoa. In conclusion, our results could be indicating that (1) spermatozoa in this species have high levels of oxidative stress regardless of whether the males were wild or born in captivity, and these high levels of ROS could be an early indicator of susceptibility to damage but (2) in very low-quality samples, high levels of ROS are not necessarily expected because the oxidative stress process could be more advanced and specific spermatozoa damage could already be happening, producing, as an example, a direct decrease in cell viability.
However, there is a point in our study that could not be easily explained considering ROS as a factor that causes defective sperm function. When we plotted the samples, DCF+ cells vs live cells considering motility ranges (Fig. 6), we observed that fast spermatozoa samples consistently appeared with high ROS levels, whereas slow spermatozoa showed low ROS levels. Although most studies in fish address the ROS issue from a negative perspective, it is intriguing how such vulnerable cells can generate these numbers of cells that are potentially dangerous for them. In mammals, it has been established that ROS play an important physiological role in spermatozoa. It is known that low levels of ROS generation are crucial for normal sperm function and are involved in important signal transduction pathways (Aitken et al. 2012). In fact, in mouse, it has been shown that sperm lipid peroxidation using a combination of ferrous ions and ascorbate increased the fertilizing potential of mouse spermatozoa by 50% (Kodama et al. 1996). Moreover, it is also known that ROS are required for compacting sperm chromatin and, paradoxically, providing protection against oxidative DNA damage (Pfeifer et al. 2001, Aitken et al. 2012). Therefore, although the underlying mechanisms of these positive effects are yet to be completely elucidated, particularly in fish, it seems clear that ROS could also be important for the regulation of sperm function.
ROS localization is also another factor that matters. In our study, we observed that ROS colocalized with mitochondria, as expected, but it is also found in the nucleus, being a potential inductor of DNA damage (Fig. 5). When compared with ROS distribution in other marine flat fish (Scophthalmus maximus) spermatozoa, we observed higher levels of ROS in Solea senegalensis nuclei (Supplementary Materials 3 and 4). Whether this species has particularly high levels of oxidative stress in their spermatozoa or they are necessary for normal sperm function, we could conclude that the beneficial or detrimental effects of ROS will always be in a delicate balance and should not always be considered alarming if they are not accompanied by other negative consequences on spermatozoa.
Supplementary data
This is linked to the online version of the paper at http://dx.doi.org/10.1530/REP-16-0270.
Declaration of interest
The authors declare that there is no conflict of interest that could be perceived as prejudicing the impartiality of the research reported.
Funding
This work was financially supported by AGL2015 68330-C2-1-R project (MINECO/FEDER).
Acknowledgements
The authors would like to acknowledge AQUAGAMETE FA 1205 COST Action, Junta de Castilla y León (EDU1084/2012) and Fondo Social Europeo, Dr Olvido Chereguini for kindly providing S. maximus sperm samples for confocal microscopy, Mariano de la Hera, Planta de Cultivos el Bocal (IEO) staff, Drs Millán Cortizo and Enrique Fernández.
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