Fish Physiol Biochem (2016) 42:869–882 DOI 10.1007/s10695-015-0181-3 Aerobic and anaerobic enzymatic activity of orange roughy (Hoplostethus atlanticus) and alfonsino (Beryx splendens) from the Juan Fernandez seamounts area L. M. Saavedra . R. A. Quiñones . R. R. Gonzalez-Saldı́a . E. J. Niklitschek Received: 8 September 2015 / Accepted: 10 December 2015 / Published online: 19 December 2015 Ó Springer Science+Business Media Dordrecht 2015 Abstract The aerobic and anaerobic enzymatic activity of two important commercial bathypelagic species living in the Juan Fernández seamounts was analyzed: alfonsino (Beryx splendens) and orange roughy (Hoplostethus atlanticus). These seamounts are influenced by the presence of an oxygen minimum zone (OMZ) located between 160 and 250 m depth. Both species have vertical segregation; alfonsino is able to stay in the OMZ, while orange roughy remains at greater depths. In this study, we compare the aerobic and anaerobic capacity of these species, measuring the activity of key metabolic enzymes in different body tissues (muscle, heart, brain and liver). Alfonsino has higher anaerobic potential in its white muscle due to greater lactate dehydrogenase (LDH) activity (190.2 lmol NADH min-1 g ww-1), which is related to its smaller body size, but it is also a feature shared with species that migrate through OMZs. This potential and the higher muscle citrate synthase and electron transport system activities indicate that alfonsino has greater swimming activity level than orange roughy. This species has also a high MDH/LDH ratio in its heart, brain and liver, revealing a potential capacity to conduct aerobic metabolism in these organs under prolonged periods of environmental low oxygen conditions, preventing lactic acid accumulation. With these metabolic characteristics, alfonsino may have increased swimming activity to migrate and also could stay for a period of time in the OMZ. The observed differences between alfonsino and orange roughy with respect to their aerobic and anaerobic enzymatic activity are consistent with their characteristic vertical distributions and feeding behaviors. L. M. Saavedra (&) Center for the Study of Multiple-Drivers on Marine SocioEcological Systems (MUSELS), Universidad de Concepción, Barrio Universitario S/N, Concepción, Chile e-mail: [email protected] R. R. Gonzalez-Saldı́a Unidad de Biotecnologı́a Marina, Facultad de Ciencias Naturales y Oceanográficas, Universidad de Concepción, Casilla 160C, Concepción, Chile R. A. Quiñones Interdisciplinary Center for Aquaculture Research (INCAR), Universidad de Concepción, O’Higgins 1695, Concepción, Chile E. J. Niklitschek Centro i*mar, Universidad de Los Lagos, Camino a Chinquihue Km 6, Casilla 557, Puerto Montt, ChileX Región R. A. Quiñones Departamento de Oceanografı́a, Facultad de Ciencias Naturales y Oceanográficas, Universidad de Concepción, Casilla 160C, Concepción, Chile 123 870 Keywords Seamounts Enzymatic activity Oxygen minimum zone Beryx splendens Hoplostethus atlanticus Introduction Seamounts are highly productive ecosystems in which the upwelling of nutrient-rich water and the trapping of diurnally migrating plankton (Rogers 1994) provide a unique deep-sea environment for fishes and invertebrates (Koslow 1997). In spite of the large number of seamounts in the global ocean, especially in the Pacific, relatively few studies have been carried out on the biology and ecology of seamount biota (Clark et al. 2014). A stable and persistent feature of seamounts located in the eastern Pacific is the presence of a permanent oxygen minimum zone (OMZ) (Rabalais et al. 2010). Therefore fish inhabiting or crossing this layer as part of their daily routine are expected to exhibit metabolic and physiological adaptations, which are still poorly understood (Martı́nez et al. 2011). This understanding has become more relevant today when the increment in hypoxic zones in the ocean worldwide has become a global issue (Zhang et al. 2010; Diaz and Rosenberg 2008; Rabalais et al. 2010), which due to global warming could become more acute in the future (Justic et al. 1996; Diaz and Rosenberg 2008; Hansen and Bendtsen 2009; Falkowski et al. 2011). An important group of Eastern Pacific seamounts corresponds to the Juan Fernandez Ridge, located on the Nazca Plate off the coast of Chile between 32–34°S and 73–82°W (Pilger 1981). Here the OMZ is composed of equatorial subsurface waters (Ahumada and Chuecas 1979), ranges between 150 and 350 m depth and presents dissolved oxygen values between 0.3 and 2.0 mL O2 L-1 (Fig. 1a) (Niklitschek et al. 2007). Below this depth, oxygen levels increase to a maximum of approximately 4 mL O2 L-1 around 600 m and decrease again to about 2 mL O2 L-1 at a depth of approximately 950 m (Chiang and Quiñones 2007; Niklitschek et al. 2007). Two commercially important bathypelagic species are exploited in this ridge, orange roughy [Hoplostethus atlanticus (Collet)] and alfonsino [Beryx splendens (Lowe)], which exhibit clear vertical segregation with only a slight overlap between 550 and 650 m (Niklitschek et al. 2007, Fig. 1b, c). Orange 123 Fish Physiol Biochem (2016) 42:869–882 roughy is bathypelagic and lives below the OMZ at preferred depths of 500–1000 m, whereas alfonsino uses shallower habitats, with greater presence around 400 m (Niklitschek et al. 2007; Guerrero and Arana 2009) and daily migrations into more superficial waters (Vinnichenko 1997), entering and crossing the OMZ on a daily basis (Fig. 1). This vertical segregation between the habitats used by the species should be reflected in important differences in their metabolic properties (Siebenaller and Somero 1989). For instance, interspecific comparisons of enzymatic activity have shown a general pattern of decreasing metabolic activity with increasing depth (Siebenaller and Somero 1989; Childress and Thuesen 1992). Moreover, vertically migratory fishes such as alfonsino are expected to have metabolic adaptations that allow them to cross and remain in the OMZ (Childress and Seibel 1998), as this zone is known to be an important barrier for the distribution of marine organisms (White 1987; Eissler and Quiñones 1999; González and Quiñones 2002). Adaptations to low oxygen availability in biota dwelling permanently or semipermanently in OMZ may be achieved using several strategies, such as (1) more effective oxygen incorporation, (2) less metabolic demand and (3) conducting anaerobic metabolism (Childress and Seibel 1998). It has also been suggested that some vertically migrating species can alternate between anaerobic metabolism while in the OMZ and aerobic metabolism when they encounter more oxygenated waters (Childress 1977). An important enzymatic adaptation to hypoxia is the change in affinity of enzymes involved in glycolysis and other pathways of carbohydrate metabolism (Panepucci et al. 2000; Wu 2002; Pollock et al. 2007). Analysis of enzyme activities can be used as an approach to assess reliance on anaerobic metabolism in OMZ species (Childress and Seibel 1998; Yang et al. 1992), as well as to determine metabolic differences between fish that have different patterns of vertical distribution (Childress and Somero 1979; Siebenaller et al. 1982; Vetter et al. 1994; Childress 1995; Vetter and Lynn 1997). For, instance, citrate synthase (CS), associated with oxidative phosphorylation, is used as an indicator of aerobic metabolism, and lactate dehydrogenase (LDH) is indicative of anaerobic metabolism (Childress 1995; Farwell et al. 2007; Martı́nez et al. 2011). Malate dehydrogenase (MDH) plays a role in both aerobic and anaerobic Fish Physiol Biochem (2016) 42:869–882 871 Fig. 1 a Dissolved oxygen profile from a zonal transect (75°W to 78.8°W) of Juan Fernandez seamounts; b vertical distribution of alfonsino and c orange roughy in these seamounts (extracted from Niklitschek et al. 2007) pathways (Vetter et al. 1994), because the mitochondrial isozyme (m-MDH) is a component of the Krebs cycle and also passes reduced equivalents between the mitochondria and the cytoplasm. The cytoplasmic isozyme (s-MDH) shares the mentioned function with m-MDH and in certain species can be important for maintaining the cytoplasmatic redox balance during intense anaerobiosis (Hochachka and Somero 1984). In this paper, we analyze and compare the activity of different metabolic enzymes in several tissues of H. Atlanticus and B. Splendens collected at the Juan Fernandez Ridge. We also estimate and compare metabolic rates through the activity of the electron transport system (ETS), which is a measure of respiration potential (Ikeda et al. 2006). Thus we characterize metabolic differences between species and explore hypotheses about the value of such differences as adaptive mechanisms making possible fairly distinct habitat use patterns under such strong gradients in hypoxic conditions. Materials and methods Collection and preservation of study animals Fish samples were obtained from deep-bottom trawls deployed between July 30 and August 7, 2005, by the 123 872 Fish Physiol Biochem (2016) 42:869–882 Fig. 2 Map showing the sampling sites. The three seamounts (JF2, JF3 and JF4) belong to the Juan Fernandez Archipelago. Coordinates correspond to UTM zone 18S factory vessel ‘‘Betanzos,’’ as part of the 2005 annual orange roughy–alfonsino hydroacoustic survey (Niklitschek et al. 2006). The sampling area included three seamounts (JF2, JF3 and JF4), all in the Juan Fernandez Ridge area (Fig. 2). A total of 24 orange roughy samples were obtained between 714 and 1178 m from seamounts JF3 and JF4; 10 alfonsino 123 samples were collected between 350 and 450 m from JF2 (Table 1; Fig. 2). These sampling depth ranges represented frequent catch strata for these two species in the study area. Once caught, each specimen was quickly sized (fork length, FL) and sections of white muscle, liver, brain and heart were extracted and immediately stored Fish Physiol Biochem (2016) 42:869–882 873 Table 1 Classifications, depth range, mean weight and capture location of sampled individuals per species Specie Class Order Family Sampling location Depth range (m) Average weight (g) Hoplostethus atlanticus Actinopterygii Beryciformes Trachichthyidae JF3, JF4 400–1800 2080 Beryx splendens Actinopterygii Beryciformes Berycidae JF2 30–850 820 in liquid nitrogen (-190 °C) for further enzymatic analysis. The rest of each fish was kept on ice until they were weighed in the laboratory on land. MDH activity (from oxaloacetate to malate) was measured in all tissues using the procedure described by Childress and Somero (1979) and Vetter et al. (1994). Homogenization Tissue samples were thawed, weighed and homogenized in 200 mM K2HPO4 buffer (pH 7.9), 0.3 % polyvinylpyrrolidone (PVP), 5 mM EDTA and 0.1 % Triton X-100, using an Ultra Turrax homogenizer in an ice bath. The amount of buffer solution that was added to each sample was calculated using a dilution factor that varied between species and tissues: orange roughy = 1:40 for muscle and brain and 1:100 for liver and heart; alfonsino = 1:67 for liver and brain and 1:100 for muscle and heart. After centrifugation of the homogenate for 5 min at 3000 g (4 °C), one part of the supernatant was used for electron transport system (ETS) analysis and the rest for measuring enzymatic activity. Determination of enzymatic activities involved in anaerobic metabolism Determination of enzymatic activities involved in aerobic metabolism The activity of the citrate synthase (CS) enzyme was measured using a modified version of the method proposed by Childress and Somero (1979) and Vetter et al. (1994). The reaction mixture contained 50 mM Imidazol/HCl pH 8.0 at 20 °C, 1.5 mM MgSO4, 0.1 mM acid, 5.5 mM dithiobis (2-nitrobenzoic) (DTNB) and 0.06 mM acetyl-CoA. The supernatant was added, and the mixture was incubated for 20 min at room temperature. Then 0.2 mM oxalacetate was added, and absorbance was measured. Absorbance was determined at 412 nm. All determinations were corrected using a blank containing the supernatant but in absence of oxalacetate. Electron transport system (ETS) activity Measurements of the various enzyme activities were conducted by spectrophotometry and run in triplicate. Assay temperature was between 15 and 16 °C. Lactate pathway activity (LDH) was analyzed as representative of anaerobic metabolism. The lactate pathway maintains its metabolic rate under hypoxic environmental or physiological conditions (Livingstone 1983). The assay mixture was modified from Schiedek (1997); it contained 80 mM K2HPO4 buffer (pH 7.9) and 3.2 mM pyruvate. Before measuring, 0.2 mM NADH was added to the mixture. Finally, an aliquot of supernatant was added and the decay of the NADH absorption at 340 nm was measured. All the enzymatic activities were corrected for nonspecific NADH oxidation. ETS was estimated using the technique described by Packard (1971). This is an indirect enzymatic method used to estimate the rate of oxygen consumption as an expression of the maximum potential activity of the electron transporters in the respiratory chain at a mitochondrial level. In situ ETS activity was calculated with the Arrhenius equation (S = A exp (Ea/k (1/Ta - 1/Ts))), where S is the in situ ETS, A is the ETS calculated at the assay incubation temperature, Ea is the Arrhenius activation energy, k is the gas constant (1.987 cal mol-1 deg-1), Ta is the assay temperature (°K) and Ts is the in situ temperature (°K). The activation energy used was 16.2 (kcal mol-1) (Arı́stegui and Montero 1995). The in situ temperature was 123 874 obtained from CTD data collected during the cruise (Niklitschek et al. 2006). All potential activities were expressed as wet weight-specific activities. Thus the unit used to express LDH and MDH activity was lmol NADH min-1 g-1wet weight (ww), CS activity was expressed as lmol DTNB min-1 g -1, and ETS as lL O2 h-1 g-1. Statistical analysis One-way analysis of variance (ANOVA) was used to evaluate differences in enzymatic activity between species, within tissues and between tissues within species. Analysis of covariance (ANCOVA) was used to evaluate species and body mass effects on the differences between enzymatic activities in fishes. Fish Physiol Biochem (2016) 42:869–882 MDH was greater in alfonsino than in orange roughy for all tissues analyzed (p \ 0.05) (Fig. 3b). ANCOVA analysis confirmed significant differences between species and showed no evidence of significant body mass effects upon MDH activity in white muscle (Table 3; Fig. 4b). White muscle exhibited greater LDH than MDH activity in both species (Fig. 5). In all other tissues, MDH activity was higher than LDH activity. The MDH/LDH ratio exhibited a similar pattern in both species, being lower in the muscle, intermediate in the heart and higher in the brain (Table 4; Fig. 6). It should be noted that this ratio was higher in all alfonsino tissues than in orange roughy tissues. Liver tissue showed a very high MDH/LDH ratio in alfonsino which was related to very low LDH activity, while in orange roughy liver MDH/LDH ratio could not be determined due to the absence of detectable LDH activity in this tissue. Results LDH Considering all tissues analyzed, LDH activity ranged between 50.4–153 lmol NADH min-1 g ww-1 in orange roughy and 4.1–190.2 lmol NADH min-1 g ww-1 in alfonsino (Table 2; Fig. 3a). LDH activity in white muscle was significantly greater in alfonsino than in orange roughy (p B 0.01), while all other tissues showed similar enzymatic activities between species (Fig. 3a). Between tissues, within species, orange roughy showed more LDH activity only in the heart, whereas in alfonsino the activity of this enzyme was greater in both white muscle and heart. In both species, LDH activity was rather low in the brain and very low or null in the liver (Table 2). ANCOVA analysis confirmed significant differences between species and showed that only for LDH in muscle the differences between both species are size related, with lower activity in heavier fishes (Table 3; Fig. 4a). CS Considering all tissues, CS activity ranged between 0.55 and 3.3 lmol DTNB min-1 g ww-1 in orange roughy and 3.31–14 lmol DTNB min-1 g ww-1 in alfonsino (Table 2; Fig. 3c). The activity of this enzyme was greater in almost all tissues of alfonsino compared with those of orange roughy, with significant differences (p \ 0.05) in muscle, heart and brain (Fig. 3c). Orange roughy presented similar CS activity in heart, brain and liver tissues; all these were greater than white muscle. Alfonsino showed very high CS activity in its heart, which was greater than in all other alfonsino tissues and significantly greater than in orange roughy white muscle (p \ 0.001) (Fig. 3c). ANCOVA analysis confirmed significant differences between species, but showed no evidence of significant body mass effects upon CS activity in white muscle (Table 3; Fig. 4b). MDH ETS Considering all tissues analyzed, MDH activity ranged between 10.3 and 236 lmol NADH min-1 g ww-1 in orange roughy and 87–519 lmol NADH min-1 g ww-1 in alfonsino (Table 2; Fig. 3b). This enzyme showed lower activity than LDH in white muscle for both species. 123 Considering all tissues analyzed, ETS activity ranged between 9.76–1261.4 ll O2 h-1 g ww-1 in orange roughy and 236–1657 ll O2 h-1 g ww-1 in alfonsino (Table 2; Fig. 3d). Fish Physiol Biochem (2016) 42:869–882 875 Table 2 Mean enzymatic activities in tissues of three different bathypelagic teleosts (±S.D) Weight (g) n Muscle n Heart 153.1 ± 85 n Brain 22 50.423 ± 12 n Liver H. atlanticus LDH 2042 25 66.2 ± 26 18 21 n.d MDH ETS in situ 2042 2067 24 23 10.3 ± 3.5 46 ± 27.1 18 18 180 ± 88 506 ± 276 21 19 170.3 ± 32 652 ± 150 21 17 236 ± 57.4 624.1 ± 146.8 CS 2055 23 0.55 ± 0.2 18 2.76 ± 1.1 19 3.3 ± 0.7 17 2.62 ± 0.5 LDH 820 10 190.2 ± 62 10 144.2 ± 73 10 41.4 ± 7 8 4.1 ± 1.3 MDH 820 9 87 ± 18 10 519.3 ± 196 10 267.3 ± 39 8 337 ± 67 236.2 ± 60 7 1657 ± 492 6 712 ± 130.6 4 803 ± 222 9 14 ± 5 9 6.2 ± 1.6 7 3.32 ± 0.5 B. splendens ETS in situ 820 8 CS 820 9 3.31 ± 0.66 Units of activity are in lmoles NADH min-1 g ww-1 for LDH and MDH, in lmoles DTNB min-1 g ww-1 for CS and in ll O2 h-1 g ww-1 for ETS Fig. 3 Activities of a LDH, b MDH, c CS and d ETS in different tissues of orange roughy Hoplostethus atlanticus and alfonsino Beryx splendens. Significant differences between species indicated with asterisks (*p \ 0.05), (**p \ 0.001) As for CS and MDH, the activity of ETS was lower in white muscle from both species, and highest in alfonsino heart tissue. This ETS activity was, in fact, significantly greater than the level observed in orange roughy heart tissue (Fig. 3d). ANCOVA confirmed significant differences in ETS activity in white muscle 123 876 Table 3 Marginal analyses of covariance (Type II) to evaluate the effects of species, body mass and their interaction upon LDH, MDH, CS and ETS activity in white muscle Fish Physiol Biochem (2016) 42:869–882 Effect Sum of squares DF F p value (p [ F) LDH muscle (R2 = 0.58) [0.1 Species 0.04302 1 2.1823 log10 (body mass) 0.13221 1 6.7073 <0.05 Species 9 log10 (body mass) 0.01119 1 0.5676 [0.4 Residuals 0.59134 30 Species 0.99528 1 85.7131 log10 (body mass) Species 9 log10 (body mass) 0.00127 0.01774 1 1 0.1095 1.5274 Residuals 0.31352 27 Species 0.44812 1 45.5447 log10 (body mass) 0.07723 1 7.8494 <0.01 Species 9 log10 (body mass) 0.00533 1 0.5422 [0.4 Residuals 0.26566 27 Species 1.09827 1 15.7797 log10 (body mass) 0.05264 1 0.7563 [0.3 Species 9 log10 (body mass) 0.03210 1 0.4613 [0.5 Residuals 1.87920 27 2 MDH muscle (R = 0.94) <0.0001 [0.7 [0.2 2 CS muscle (R = 0.94) <0.0001 ETS muscle (R2 = 0.63) Bold font highlights significant effects between species, but showed no relationship to body weight (Fig. 4d). Considering the enzyme activity of the electron transfer system to be a measure of respiration potential (Ikeda 1996; Ikeda et al. 2006), a positive correlation was observed between enzymatic activity and respiration rate considering the species together, indicating a linear increment in enzyme activity with higher respiration rate (Fig. 7). Discussion Seamounts are relatively common features on the ocean floor, which concentrate high ecological, economical and scientific interest. However, relatively few studies have been performed on the ecology of these ecosystems and the biology of their biota. This study focused on some metabolic characteristics in two of the most abundant fishes inhabiting seamounts in the eastern South Pacific and elsewhere, finding clear differences in enzymatic activities involved in anaerobic and aerobic metabolism. These differences were consistent with expectations derived from known differences between these two species with respect to 123 <0.001 their (1) habitat depth (*250 m between distribution modes) and oxygen availability (*2 mg l-1); and (2) behavior, including predation and presence/absence of daily vertical migration. The higher levels of LDH activity we found in alfonsino white muscle seem to be mainly related to a body mass effect. This was not, however, the case of MDH, CS and ETS, whose higher activity in several alfonsino tissues exceeded differences due to potential body mass effects and was consistent with the general expectation of greater activity of metabolic enzymes in shallower species (Childress and Somero 1979; Somero 1992; Siebenaller et al. 1982; Childress 1995; Vetter et al. 1994; Vetter and Lynn 1997; Drazen and Seibel 2007). Nonetheless, due to our sampling design (i.e., limited sampling opportunities), it was not possible to separate species effects from depth effects.LDH activity was very similar between both species for heart, brain and liver, while in white muscle, LDH showed the expected tendency for depth inhabiting fishes (Vetter et al. 1994), with a higher anaerobic activity in smaller fishes (alfonsino). The higher CS levels found in all alfonsino tissues are indicating a higher aerobic potential of this fish, which is consistent with his increased swimming capacity, Fish Physiol Biochem (2016) 42:869–882 877 Fig. 4 Relationship between enzymatic activity in white muscle and body mass for a LDH, b MDH, c CS and d ETS in alfonsino [(open circle) Beryx splendens] and orange roughy [(filled circle) Hoplostethus atlanticus]. Regression lines and expected values, represented as YALF and YOR, for alfonsino and orange roughy, respectively, correspond to the best model, selected for each enzyme using a stepwise backwards procedure (alpha = 0.05) including prolonged burst swimming (Niklitschek et al. 2007). High MDH/LDH ratios may cause an attenuated pyruvate to lactate flux. As a consequence, carbohydrate metabolism will be largely channeled toward complete oxidation (Almeida-Val and Hochachka 1993). Therefore, the MDH/LDH ratios much [1 we observed in heart and brain tissues in both species, particularly in alfonsino, indicate enhanced capacity to maintain cytoplasmatic redox balance during intense anaerobiosis, suggesting evolutionary adaptation to protect these important organs under hypoxic and anoxic conditions (Shapiro and Bobkova 1975; Panepucci et al. 2000; Panepucci et al. 2001). In contrast, the low MDH/LDH ratios we found in white muscle tissue of both species suggest efficient 123 878 Fish Physiol Biochem (2016) 42:869–882 Fig. 6 MDH/LDH ratios in different tissues off H. atlanticus and B. splendens. Significant difference between species indicated with an asterisk (p \ 0.05) Fig. 5 Differences between lactate dehydrogenase (LDH) and malate dehydrogenase (MDH) activity in different tissues from a alfonsino (B. splendens) and b orange roughy (H. atlanticus). Values are mean ± SD. Significant differences between enzymes are given by *(p \ 0.01), ***(p \ 0.0001) Table 4 Ratios of MDH/LDH activity for two bathypelagic species n MDH/LDH Muscle Heart Brain H. atlanticus 20 0.181 (0.12) 1.16 (0.3) 3.47 (0.6) B. splendens 10 0.518 (0.2) 3.4 (0.9) 6.63 (1.4) Data are expressed as mean and S.E.M anaerobic production of ATP in this tissue regardless of oxygen availability in the water column or the plasma. These results agree with those of Panepucci et al. (2000), who found high MDH/LDH ratio in heart and brain of Rhinelepis strigosas exposed to different oxygen levels, showing the importance of these organs for the survival of this species when subjected to extreme hypoxic conditions. The higher MDH/LDH ratios observed in alfonsino for almost all tissues provide support to the idea that alfonsino is more adapted to withstand hypoxic conditions than orange 123 roughy, allowing him to cross and to stay in the OMZ (Torres et al. 2012). In terms of aerobic enzymatic activity, white muscle showed the lowest levels of CS and ETS activity in both species, which was expected because of the physiology of this tissue (Somero and Childress 1980). This reaffirms the predominance of aerobic metabolism in all analyzed tissues except the muscle. The white muscle, heart and brain tissues showed significantly higher CS activity in alfonsino than in orange roughy, which is consistent with higher MDH levels in these tissues and could be associated with greater capacity for sustained swimming, even under low oxygen conditions (Sullivan and Somero 1980). Moreover, observed differences in ETS activity in white muscle would be indicative of a greater respiratory rate in alfonsino (Ikeda 1996), which would be consistent with a more active feeding strategy and a higher habitat temperature. Considering the enzyme activity of the electron transfer system to be a measure of respiration potential (Ikeda 1996; Ikeda et al. 2006), the very strong correlations found between muscle enzymatic activities and whole fish respiration rate (expressed as ETS) suggest that the lower respiratory rate estimated for orange roughy is principally due to reduced potential for enzymatic activity in its white muscle. This correlation is also in agreement with the results of Childress and Somero (1979), which showed that muscle enzymatic activity may provide a valid estimate of the VO2 of fish that cannot be recovered alive (e.g., fishes that have swim bladders and embolize during transit to the surface). All previous results about enhanced tolerance to hypoxia and increased metabolic rate in alfonsino are Fish Physiol Biochem (2016) 42:869–882 879 Fig. 7 Correlation between enzymatic activities and respiration rate measured as ETS (ll O2 h-1 g-1). (open circle) Orange roughy and (filled circle) alfonsino also consistent with observations indicating that this specie is capable to conduct daily feeding migrations connected to the daily migrations of its prey, mainly euphausiids and cephalopods (Vinnichenko 1997; Alabsi 2011). To conduct this vertical migration, alfonsino would take advantage of the previously described ability to cross the OMZ, which is a pervasive feature of the water column in the study area (Niklitschek et al. 2007). However, this hypothesis remains to be tested through direct behavioral studies in the Juan Fernandez seamounts area. We found a rather weak relationship between enzymatic activity and body weight for most enzymes and tissues, where significant body mass effects were found only for LDH and CS in white muscle and for MDH in brain tissue (not shown in our results). Both enzymes (LDH and CS) showed a decrease in activity with increasing body weight, which is consistent with Vetter et al. (1994) who found that enzymatic activities decreased with increasing body size in flatfishes inhabiting the continental slope ([400 m), presumably reflecting lower activity and growth in the deep-living adult population. However, it is impossible to make any sound inference about allometry from our study due to the similarity in the body sizes of the organisms caught; a larger sample size and a wider body mass range would be required to be more conclusive about these relationships. Although we could not demonstrate that the differences observed in enzymatic activity between the species are due to habitat differences, we hypothesize that vertical distribution (and therefore pressure) plays a significant role in metabolism. In fact, orange roughy lives below 600 m, with modes at 650 and 850 m, while alfonsino remains above 500 m, with a strong mode at 450 m. Daylight only penetrates the upper 1000 m in the ocean and declines exponentially with depth (Warrant and Locket 2004). Thus, the lower metabolic activity of orange roughy might be partially explained by a reduced ‘‘visual interaction’’ with its prey. This hypothesis, proposed by Childress (1995), predicts a rapid decline in metabolic rate with increasing depth in deep-living animals with developed visual perception systems (e.g., eyes). This would be due to the effects of downward light diminishing upon prey– predator reaction distance, resulting in a progressive reduction in energy expenditure with increasing depth (Ikeda et al. 2006). Another important factor that might be affecting the metabolic rate of these two species is temperature (Yang et al. 1992). However, since orange roughy lives at 2–6 °C and alfonsino lives between 6 and 11 °C (Niklitshek et al. 2007), the difference between the average temperatures where these species inhabit is not enough (4 °C in average) to explain any effect on their metabolic rate. The greater activity of metabolic enzymes observed in alfonsino contradicts the expectation that reduced metabolic rates may represent suitable adaptations to confront low oxygen levels in the OMZ (Childress and Seibel 1998), providing evidence that an enhanced glycolytic power may instead be the adaptive mechanism or phenotypic response used by some fishes inhabiting or visiting the OMZ on a regular basis. This result is similar to that of Yang and Somero (1993), who found a much higher LDH activity in red muscle of Sebastolobus alascanus living in the OMZ, which they interpreted as a phenotypic response to habitat hypoxia. As in the present study, they found no evidence of greater anaerobic poise in the brain of OMZ species than in the brain of species inhabiting shallower waters. The same trend was reported by Torres et al. (2012) comparing fish of systems with 123 880 different oxygen levels, where Arabic Sea species had much greater LDH activity than fish from the Gulf of Mexico. It is important to note that the biochemical indicators found in the present study are not sufficient to establish with certainty that alfonsino is particularly adapted to crossing or visiting the OMZ. In fact, as mentioned before, the greater anaerobic and aerobic capacity observed in its white muscle and the enzymatic protection of its vital organs against hypoxia may be just primary responses or adaptations that allow increased swimming activity, related to an active feeding behavior including its daily feeding migrations. To prove increased tolerance to habitat hypoxia, other indicators such as circulatory and morphological adaptations should be investigated and compared between species, including gill surface areas, ventilation rate and volumes and the affinity for oxygen of their respiratory proteins (Childress and Seibel 1998; Seibel et al. 1999). In conclusion, alfonsino exhibited greater anaerobic potential in its white muscle than orange roughy, a potential that seems shared with other species that migrate through OMZs elsewhere (Yang et al. 1992; Vetter and Lynn 1997; Torres et al. 2012). This potential and the higher white muscle CS and ETS activities indicate that alfonsino also has a higher swimming activity level than orange roughy. Moreover, this species has a high MDH/LDH ratio in its heart, brain and liver, revealing a greater potential to conduct aerobic metabolism in these organs under prolonged periods of fast swimming and/or environmental low oxygen conditions, preventing lactic acid accumulation. All these metabolic differences made it possible for alfonsino and probably not possible for orange roughy to migrate through and sometimes remain for a certain period of time in the OMZ. Acknowledgments This research was funded by the Interdisciplinary Center for Aquaculture Research (INCAR; FONDAP 1511002). Sampling was made possible as part of research Project No 2004–13 from the Fondo de Investigación Pesquera, Chile (Undersecretariat of Fisheries, Ministry of Economy, Chile). R. Gonzalez was funded by FONDECYT 234568 (CONICYT, Chile), E. Niklitschek by INNOVA Chile Grant No. 34567 and Luisa Saavedra by FONDECYT 3150392 and Center for the study of multiple-drivers on marine socioecological systems (MUSELS, IC120019). Funding This study was funded by Fondo de Investigación Pesquera, Chile (Undersecretariat of Fisheries, Ministry of Economy, Chile) research Project No. 2004–13, Interdisciplinary 123 Fish Physiol Biochem (2016) 42:869–882 Center for Aquaculture Research (INCAR; FONDAP 1511002) and FONDECYT 3150392. Compliance with ethical standards Conflict of interest The authors declare that they have no conflict of interest. Research involving human participants and/or animals The fishes used in this research were collected from deep-bottom trawls deployed by the factory vessel ‘‘Betanzos,’’ as part of the 2005 annual orange roughy–alfonsino hydroacoustic survey. The specimens were obtained from the trawls. Subsequently they were anaesthetized using benzocaine. Once they were fully anesthetized, they were dissected and tissues and organs preserved in liquid nitrogen. The fish died due to the removal of the heart, a needed tissue for the experimental objective. We did not conduct experimental work with animals alive. We only used tissues preserved in liquid nitrogen. In any case, all our experimental procedures at the laboratory are in agreement with the regulations of the Chilean National Commission on Scientific and Technological Research (CONICYT), Ministry of Education, Chilean Government. References Ahumada R, Chuecas L (1979) Algunas caracterı́sticas hidrográficas de la Bahı́a Concepción (36°400 S; 73°020 W) y áreas adyacentes (Chile). Gayana 8:1–56 Alabsi NM (2011) Studies on the behavior of a deep-water fish, the splendid alfonsino (Beryx splendens) using micro data loggers. Master thesis University of Tokyo Almeida-Val VMF, Hochachka PW (1993) Hypoxia tolerance in Amazon fishes: status of an underexplored biological ‘‘goldmine’’. In: Hochachka PW, Lutz PL, Sick T, Rosenthal M, Van den Thillart G (eds) Surviving hypoxia: mechanisms of control and adaptation. CRC Press, Boca Raton, pp 435–445 Arı́stegui J, Montero MF (1995) The relationship between community respiration and ETS activity in the ocean. J Plankton Res 17:1563–1571 Chiang OE, Quiñones RA (2007) Relationship between viral and prokaryotic abundance on the Bajo O’Higgins 1 Seamount (Eastern South Pacific, Chile). Sci Mar 71:37–46 Childress JJ (1977) Effects of pressure, temperature and oxygen on the oxygen consumption rate of the midwater copepod Gaussia princeps. Mar Biol 39:19–24 Childress JJ (1995) Are there physiological and biochemical adaptations of metabolism in deep-sea animals? Tree 10:30–36 Childress JJ, Seibel BA (1998) Life at stable low oxygen levels: adaptations of animals to oceanic oxygen minimum layers. J Exp Biol 201:1223–1232 Childress JJ, Somero GN (1979) Depth-related enzymic activities in muscle, brain and heart of deep-living pelagic marine teleosts. Mar Biol 52:273–283 Fish Physiol Biochem (2016) 42:869–882 Childress JJ, Thuesen EV (1992) Metabolic potential of deepsea animals: regional and global scales. In: Rowe GT, Parient V (eds) Deep Sea food chains and the global carbon cycle. Kluwer Academic publishers, Berlin, pp 217–236 Childress JJ, Taylor SM, Cailliet GM, Price MH (1980) Patterns of growth, energy utilization and reproduction in some meso-and bathypelagic fishes off the Southern California. Mar Biol 61:27–40 Clark MR, Rowden AA, Schlacher TA, Guinotte J, Dunstan PK, Williams A, O’Hara TD, Watling L, Niklitschek E, Tsuchida S (2014) Identifying ecologically or biologically significant areas (EBSA): a systematic method and its application to seamounts in the South Pacific Ocean. Ocean Coast Manag 91:65–79 Diaz RJ, Rosenberg R (2008) Spreading dead zones and consequences for marine ecosystems. Science 321:926–929 Drazen JC, Seibel BA (2007) Depth-related trends in metabolism of benthic and benthopelagic deep-sea fishes. Limnol Oceanogr 52:2306–2316 Eissler Y, Quiñones RA (1999) Microplanktonic respiration off northern Chile during El Niño 1997-1998. J Plankton Res 21:2263–2283 Falkowski PG, Algeo T, Codispoti L, Deutsch C, Emerson S, Hales B, Huey B, Jenkins WJ, Kump R, Levin A, Lyons TW, Nelson NB, Schofield OS, Summons R, Talley LD, Thomas E, Whitney F, Pilcher CB (2011) Ocean deoxygenation: past, present and future. EOS 92(46):409–420 Farwell M, Fox MG, Moyes ChD, Burness G (2007) Can hypoxia tolerance explain differences in distribution of two co-occurring north temperate sunfishes? Environ Biol Fish 78(1):83–90. doi:10.1007/s10641-006-9079-3 González RR, Quiñones RA (2002) Ldh activity in Eupausia mucronata and Calanus chilensis: implications for vertical migration behaviour. J Plankton Res 24:1349–1356 Guerrero A, Arana P (2009) Fishing yields, size structures, and sexual maturity of alfonsino (Beryx splendens) caught on Juan Fernandez seamounts Chile. Lat Am J Aquat Res 37(3):463–478 Hansen JLS, Bendtsen J (2009) Effects of climate change on hypoxia in the North Sea—Baltic Sea transition zone. IOP conference series and Earth Environmental Science vol 6, p 302016 Hochachka PW, Somero GN (1984) Biochemical adaptation. Princeton University Press, Princeton, p 538 Ikeda T (1996) Metabolism, body composition, and energy budget of the mesopelagic fish Maurolicus muelleri in the sea of Japan. Fish B NOAA 94:49–58 Ikeda T, Sano F, Yamaguchi A, Matsuishi T (2006) Metabolism of mesopelagic and bathypelagic copepods in the western North Pacific Ocean. Mar Ecol Prog Ser 322:199–211 Justic D, Rabalais NN, Turner RE (1996) Effects of climate change on hypoxia in coastal waters: a doubled CO2 scenario for the Northern Gulf of Mexico. Limnol Oceanogr 41(5):992–1003 Koslow JA (1997) Seamounts and the ecology of deep-sea fisheries. Am Sci 85:168–176 Livingstone DR (1983) Invertebrate and vertebrate pathway of anaerobic metabolism: evolutionary considerations. J Geol Soc London 140:27–37 Martı́nez ML, Raynard EL, Rees BB, Chapman LJ (2011) Oxygen limitation and tissue metabolic potential of the 881 African fish Barbus neumayeri: roles of native habitat and acclimatization. Ecology 11:2 Niklitschek E, Boyer D, Cornejo J, Merino R, Hernández EA, Nelson J, Lafon A, Toledo JP (2006) Evaluación hidroacústica y TS de alfonsino y orange roughy: Informe de Avance. Fondo de Investigación Pesquera/Universidad Austral de Chile, Valparaı́so, FIP 2005–13 Niklitschek E, Cornejo J, Hernández EA, Toledo P, Herranz C, Merino R, Lafon A, Castro L, Roa R, Aedo G (2007) Evaluación hidroacústica de alfonsino y orange roughy, año 2006. Informe Final Proyecto FIP 2006–09, Universidad Austral de Chile, Coyhaique Packard TT (1971) The measurement of respiratory electrontransport activity in marine phytoplankton. J Mar Res 29:235–244 Panepucci L, Fernandes MN, Sanches JR, Rantin FT (2000) Changes in lactate dehydrogenase activities during hypoxia and after temperature acclimation in the armored fish, Rhinelepis strigosa (Siluriformes, Loricariidae). Braz J Biol 60:353–360 Panepucci RA, Panepucci L, Fernandes MN, Sanches JR, Rantin FT (2001) The effect of hipoxia and recuperation on carbohydrate metabolism in Pacu (Piaractus mesopotamicus). Braz J Biol 61:547–554 Pilger RH (1981) Plate reconstructions, aseismic ridges, and low-angle subduction beneath the Andes. Geo Soc Am Bull 92:448–456 Pollock MS, Clarke LMJ, Dubé MG (2007) The effects of hypoxia on fishes: from ecological relevance to physiological effects. Environ Rev 15:1–14 Rabalais NN, Diaz RJ, Levin LA, Turner RE, Gilbert D, Zhang J (2010) Dynamics and distribution of natural and humancaused hypoxia. Biogeosciences 7:585–619 Rogers AD (1994) The biology of seamounts. Adv Mar Biol 30:305–350 Schiedek D (1997) Marenzelleria viridis (Verril, 1873) Polychaeta, a new benthic species within European coastal waters, some metabolic features. J Exp Mar Biol Ecol 211:85–101 Seibel BA, Chausson F, Lallier FH, Zal F, Childress JJ (1999) Vampire blood: respiratory physiology of the vampire squid (Cephalopoda: Vampyromorpha) in relation to the oxygen minimum layer. Exp Biol 4:1–10 Shapiro AZ, Bobkova AN (1975) The role of malate dehydrogenase in adaptation to hypoxia in invertebrates. J Evol Biochem Phys 11:478–479 Siebenaller JF, Somero GN (1989) Biochemical adaptation to the deep sea. Aquat Sci 1:1–25 Siebenaller JF, Somero GN, Haedrick RL (1982) Biochemical characteristics of macrourid fishes differing in their depths of distribution. Biol Bull 163:240–249 Somero GN (1992) Biochemical ecology of deep-sea animals. Experientia 48:537–542 Somero GN, Childress JJ (1980) A violation of the metabolismsize scaling paradigm: activities of glycolytic enzymes in muscle increase in larger-size fish. Physiol Zool 53:322–337 Sullivan KM, Somero GN (1980) Enzyme activities of fish skeletal muscle and brain as influenced by depth of occurrence and habits of feeding and locomotion. Mar Biol 60:91–99 123 882 Torres JJ, Grigsby MD, Clarke ME (2012) Aerobic and anaerobic metabolism in oxygen minimum layer fishes: the role of alcohol dehydrogenase. JEB 215:1905–1914 Vetter RD, Lynn EA (1997) Bathymetric demography, enzyme activity patterns, and bioenergetics of deep-living scorpaenid fishes (genera Sebastes and Sebastolobus): paradigms revisited. Mar Ecol Prog Ser 55:173–188 Vetter RD, Lynn EA, Garza M, Costa AS (1994) Depth zonation and metabolic adaptation in Dover sole, Microstomus pacificus, and other deep-living flatfishes: factors that affect the sole. Mar Biol 120:145–159 Vinnichenko VI (1997) Vertical diurnal migrations of the slender alfonsino Beryx splendens (Berycidae) at the underwater rises of the open North Atlantic. J Ichthyol 37:438–444 Warrant E, Locket A (2004) Vision in the deep sea. Biol Rev 79:671–712 White BN (1987) Oceanic anoxic events and allopatric speciation in the deep sea. Biol Oceanogr 5:243–259 Wu RSS (2002) Hypoxia: from molecular responses to ecosystem responses. Mar Pollut Bul 45:35–45 123 Fish Physiol Biochem (2016) 42:869–882 Yang TH, Somero GN (1993) The effects of feeding and food deprivation on oxygen consumption, muscle protein concentration and activities of energy metabolism enzymes in muscle and brain of shallow-living (Scorpaena guttata) and deep-living (Sebastolobus alascanus) scorpaenid fishes. J Exp Biol 181:213–232 Yang TH, Lai NC, Graham JB, Somero GN (1992) Respiratory, blood, and heart enzymatic adaptations of Sebastolobus alascanus (Scorpaenidae; Teleostei) to the oxygen minimum zone: a comparative study. Biol Bull 183:490–499 Zhang J, Gilbert D, Gooday AJ, Levin L, Naqv SWA, Middelburg JJ, Scranton M, Ekau W, Peña A, Dewitte B, Oguz T, Monteiro PMS, Urban E, Rabalais NN, Ittekkot V, Kemp WM, Ulloa O, Elmgren R, Escobar-Briones E, Van der Plas AK (2010) Natural and human-induced hypoxia and consequences for coastal areas: synthesis and future development. Biogeosciences 7:1443–1467
© Copyright 2026 Paperzz