SEARCH

SEARCH BY CITATION

Keywords:

  • Antioxidant enzymes;
  • hydrothermal vents;
  • metallothionein;
  • Mirocaris fortunata;
  • Palaemon elegans;
  • Palaemonetes varians;
  • Ria Formosa;
  • Rimicaris exoculata;
  • shrimps

Abstract

  1. Top of page
  2. Abstract
  3. Problem
  4. Material and Methods
  5. Results
  6. Discussion
  7. Summary
  8. Acknowledgements
  9. References

Rainbow vent field is one of the most metal-contaminated hydrothermal sites on the Mid-Atlantic Ridge near the Azores region. Two hydrothermal shrimp species dominate the fauna at the Rainbow site along with the mussel Bathymodiolus azoricus. Although the levels of essential and non-essential metals in these shrimps have been studied, the biological consequences of a metal-rich environment are still largely unknown. Therefore, the aim of this study was to determine the levels of metal-binding proteins – metallothioneins (MT) and the activities of antioxidant enzymes – superoxide dismutase, catalase, total glutathione peroxidase and selenium-dependent glutathione peroxidase in two hydrothermal vent shrimps (Mirocaris fortunata and Rimicaris exoculata) collected from the Rainbow site and to compare them with two coastal shrimps (Palaemon elegans and Palaemonetes varians) from a south Portugal lagoon (Ria Formosa) to evaluate their different adaptation strategies towards metals in their environment. Results show significant differences in MT levels and antioxidant enzymatic activities between vent and coastal shrimps and also between shrimp species collected from the same site. This suggests that biochemical responses in both vent and coastal shrimps are affected not only by the environmental characteristics but also by inter-specific differences. Nevertheless, these responses apparently confer successful adaptation for survival in a metal-extreme environment.


Problem

  1. Top of page
  2. Abstract
  3. Problem
  4. Material and Methods
  5. Results
  6. Discussion
  7. Summary
  8. Acknowledgements
  9. References

Hydrothermal vent environments exhibit natural high metal concentrations as a result of the interaction between seawater and magmatic rocks. Consequently, the hydrothermal vent fluids have a very high temperature (300–350 °C) and are naturally enriched in silica (SiO2), metals (e.g. Fe, Mn, As, Cd, Cu, etc.) and dissolved gases (e.g. H2S, CH4, H2, CO2) (Von Damm 1990, 1992; Lowell et al. 1995; Von Damm et al. 1995; Sarradin et al. 1998).

The Rainbow vent field was discovered in 1997, is located at 36° 13.8′ N 33° 54.15′ W in the north AMAR (ALVIN Mid-Atlantic Ridge) segment, and is the deepest vent site located in the Azores Triple Junction area (2270–2500, 2320 m deep) (Fouquet et al. 1997; Desbruyères et al. 2001; Douville et al. 2002). The most active smokers are located at the western and the eastern ends of the hydrothermal field (Desbruyères et al. 2001). Rainbow hydrothermal fluids are uniform in composition and influenced by phase separation (Douville et al. 1999). Active chimneys, emitting hot-temperature (365 °C) acidic fluids (pH = 2.8) and that are relatively low in H2S, are arranged longitudinally along a 200-m stretch of ridge. The metal concentrations (Cu, Fe, Mn, and Zn) in Rainbow vent fluids are the highest observed in the MAR hydrothermal area (Desbruyères et al. 2000; Douville et al. 2002).

In contrast, the Ria Formosa is a highly productive mesotidal lagoon, separated from the ocean by a system of five sand barrier islands and six inlets, which extend for about 55 km along the south coast of Portugal. The average water depth is <2 m and the tidal height varies from a maximum of 3.7 m at spring tide to a minimum of 0.4 m at neap tide. Hence, most of the water volume is drained in each tidal cycle, thereby imposing a short residence time and an intense exchange of materials between the Ria Formosa and the adjacent coastal waters (Bebianno 1995; Caetano et al. 2002; Santos et al. 2004). Nevertheless, the water quality of the lagoon has deteriorated over the last decade reflecting the intense economic development of areas around the lagoon, whose major inputs of pollutants came from untreated sewage and domestic effluents from two cities (Bebianno 1995; Caetano et al. 2002).

Caridean shrimps, in particular Mirocaris fortunata (Martin & Christiansen 1995) and Rimicaris exoculata (William & Rona 1986), co-dominate populations in deep Atlantic hydrothermal fields near the Azores Triple Junction. The shrimp species M. fortunata colonize mainly sulphide diffusers, with higher densities on chimneys covered by iron oxides. In contrast, dense swarms of R. exoculata are located in small depressions between chimneys expelling superheated sulphide-loaded fluid (Gebruk et al. 1993, 2000; Segonzac et al. 1993; Polz et al. 1998; Desbruyères et al. 2001). These species have been extensively studied in terms of their abundance, density and microhabitat preferences in MAR hydrothermal vents (Gebruk et al. 1993, 2000; Segonzac et al. 1993; Desbruyères & Segonzac 1997; Polz et al. 1998), behaviour and nutritional strategies (Casanova et al. 1993; Renninger et al. 1995; Gebruk et al. 2000) and concentration of essential and non-essential metals in their tissues (Geret et al. 2002; Kádár et al. 2006). Nevertheless, the physiological responses towards metals in these species are still largely unknown. It is well recognized that metals can be toxic to organisms when present at high levels. Metals can increase the synthesis of metallothioneins (MT), which bind free metal ions (Langston et al. 1998) to form an inactive metal–MT complex and therefore these proteins are capable of detoxifying the metals inside the cells (Park et al. 2001). The accumulation of metals also enhances the production of highly toxic radical oxygen species (ROS) (Fridovich 1998), which include the superoxide anion radical (Oinline image), hydrogen peroxide (H2O2) and the highly reactive hydroxyl radical (OH), peroxyl radicals (ROO), alkoxyl radicals (RO) and peroxynitrite (HOONO) (Darley-Usmar et al. 1995). Hydrogen sulphide, known to be a potent inhibitor of antioxidant enzymes, reacts spontaneously with oxygen to generate many toxic oxygen and sulphide compounds, which in turn are capable of inflicting DNA damage (Pruski & Dixon 2003). Aerobic organisms possess a baseline status of antioxidant systems, involved in a variety of detoxification reactions, to assure the maintenance of a balance between production and removal of endogenous ROS and other pro-oxidants. This pro-oxidant/antioxidant balance and detoxification of potentially damaging ROS is crucial for cellular homeostasis (Winston & Di Giulio 1991; Lemaire & Livingstone 1993; Livingstone 2001). The activities of antioxidant enzymes were described for some hydrothermal vent species, mainly in the mussels Bathymodiolus azoricus from MAR vent fields (Bebianno et al. 2005), in the tubeworm Riftia pachyptila and in the clam Calyptogena magnifica from the East Pacific Rise vent fields (Blum & Fridovich 1984).

Nevertheless, there is still a lack of information about the antioxidant defence systems in other hydrothermal species and their relation with environmental characteristics. Therefore, the aim of this study was to address several questions regarding the metal detoxification processes in both hydrothermal and costal shrimps, namely:

  • 1
    Are MT concentrations more similar in shrimps from the same environments? Is there any relationship between MT levels and antioxidant enzyme activities?
  • 2
    Is there a relation between the metabolic responses towards metals in shrimps from different environments?
  • 3
    Can these responses be due to specific environmental parameters related to microhabitat, or to inter-specific characteristics like feeding strategies?

To answer these questions we studied the adaptation strategies towards metals, especially those regarding MT levels and activities of antioxidant enzymes in two hydrothermal vent shrimp species (M. fortunata and R. exoculata) from the Rainbow vent field. We compared the results with two euryhaline coastal shrimp species (Palaemon elegans, Rathke 1837 and Palaemonetes varians, Leach 1814), with analogous microhabitat and feeding habits, i.e. detritivores (FAO – Food and Agriculture Organization of the United Nations 1980) collected in a lagoon system (Ria Formosa).

Material and Methods

  1. Top of page
  2. Abstract
  3. Problem
  4. Material and Methods
  5. Results
  6. Discussion
  7. Summary
  8. Acknowledgements
  9. References

Two hydrothermal vent shrimp species, Rimicaris exoculata (56.89 ± 7.32 mm carapace length, n = 8) and Mirocaris fortunata (21.89 ± 2.06 mm carapace length, n = 8) were collected from the Rainbow vent site, located on the Mid-Atlantic Ridge (MAR) (36°13′ N; 33°54.1′ W, 2500 m) (Fig. 1A), using the remote operated vehicle VICTOR6000 during the SEAHMA I cruise. Additionally, two coastal shrimp species, Palaemon elegans (36.29 ± 4.18 mm carapace length, n = 8) and Palaemonetes varians (33.47 ± 2.21 mm carapace length, n = 8), were collected from the margin of the Ria Formosa lagoon system in south Portugal (37°03′ N; 07°47′ W) (Fig. 1B) with a sub-superficial tow using a shrimp net (c. 40 cm diameter). The two coastal shrimp species were sampled at the same local site. The physical–chemical comparison between the two sampling sites is presented in Table 1. Both vent and coastal shrimp species were immediately frozen in liquid nitrogen after collection and stored at −80 °C until biochemical analysis. All dissected shrimp exoskeletons and gills were separated from soft tissues.

image

Figure 1.  Location of Rainbow hydrothermal vent site in the Azores Triple Junction area (A) and Ramalhete channel in the Ria Formosa lagoon (South Portugal) (B) (adapted from Caetano et al. 2002; Santos et al. 2004; Bebianno et al. 2005).

Download figure to PowerPoint

Table 1.   Temperature, pH and concentration of chemical species in the end-member fluids of lagoon system Ria Formosa (South Portugal) and MAR vent field (Rainbow) compared with average seawater (adapted from Caetano et al. 1997; Douville et al. 2002).
SiteRia Formosa 37°03′ N; 07°47′ WRainbow 36°13′ N, 33°54′ WSeawater
T (°C)17.3a365c
pH8.28a2.8c7.8
H2S (mm)1.0c∼0
CO2(mm)< 16c
CH4(mm)2.2–2.5c∼0
Cd (nm)0.9 – 4.5a130c0.7
Cu (μm)0.02 – 0.05a140c0.0033
Zn (μm)0.02 – 0.03a160c0.028
Fe (μm)8 – 52b24000c0.0045
Mn (μm)2.5 – 6.3b2250c0.0013
Cl (mm)750c546
Co (μm)13c<2
Ag (nm)47c0.023
Ni (μm)3c<2
Si (mm)6.9c<0.2

Metallothioneins

To determine the MT concentrations, the whole soft tissues of hydrothermal and coastal shrimps were homogenized in three volumes of 0.02 m TRIS-HCl buffer (pH 8.6) in an ice bath (4 °C). An aliquot of the homogenate (3 ml) was centrifuged at 30,000 g for 1 h at 4 °C. The supernatant (cytosol) was separated from the residual fraction, heat-treated at 80 °C for 10 min to precipitate the high molecular weight ligands, and subsequently centrifuged under the conditions described above. Aliquots of the heat-treated cytosol were used for the quantification of MT concentrations by differential pulse polarography according to the method described by Bebianno & Langston (1989). MT levels are expressed as mg·g−1 total protein concentrations.

Antioxidant enzymes

Antioxidant enzymatic activities were determined in the different shrimp species' edible tissues, after homogenization in 20 mm Tris buffer, pH 7.6, containing 1 mm of EDTA, 0.5 m of saccharose, 0.15 m of KCl and 1 mm of DTT. The homogenates were centrifuged at 500 g for 15 min at 4 °C to precipitate large particles and centrifuged again at 12,000 g for 45 min at 4 °C to precipitate the mitochondrial fraction. Supernatants were purified on a Sephadex G-25 gel column to remove low molecular weight proteins.

Superoxide dismutase (SOD) activity (EC 1.15.1.1) was determined by measuring the reduction of cytochrome c by the xanthine oxidase/hypoxanthine system at 550 nm (McCord & Fridovich 1969). One unit of SOD is defined as the amount of enzyme that inhibits the reduction of cytochrome c by 50%. SOD activity is expressed in U SOD mg−1 total protein concentrations.

Catalase (CAT) activity (EC 1.11.1.6) was determined according to Greenwald (1985) by the decrease in absorbance at 240 nm because of H2O2 consumption. The CAT activity is expressed as mmoles min−1 mg−1 of total protein concentrations.

Glutathione peroxidase activities were measured following NADPH oxidation at 340 nm in the presence of excess glutathione reductase, reduced glutathione and corresponding peroxide (Lawrence & Burk 1976). The selenium-dependent glutathione peroxidase (Se-GPx) (EC 1.11.1.9) and total glutathione peroxidase (GPx) activities were measured by using respectively, H2O2 and cumene hydroperoxide as substrates. GPx activities are expressed as μmoles min−1 mg−1 of total protein concentrations.

Total protein concentrations

The whole edible tissues of vent and coastal shrimp were homogenized in 20 mm Tris buffer, pH 8.6, containing 150 mm of NaCl. The homogenates were centrifuged for 30 min at 30,000 g at 4 °C. Total protein concentrations were measured on supernatants by the Lowry method (Lowry et al. 1951) using BSA as reference standard material. Protein concentrations are expressed as mg·g−1 wet weight tissue.

The variability of MT concentrations and antioxidant enzymes activities was tested in the different species through the analysis of variance (one way-ANOVA). A Duncan test was used to determine significant differences between species for each variable. Regression analyses were also applied to assess the relationship between the concentrations of MT and antioxidant enzymes. A significance level of 0.05 was used for all statistical analysis, i.e. probability of P ≤ 0.05 was considered significant.

Results

  1. Top of page
  2. Abstract
  3. Problem
  4. Material and Methods
  5. Results
  6. Discussion
  7. Summary
  8. Acknowledgements
  9. References

In the hydrothermal vent shrimp from Rainbow, MT levels in Rimicaris exoculata (7.30 ± 0.66 mg·g−1 ww protein) were approximately sixfold higher compared with those found in Mirocaris fortunata (1.27 ± 0.27 mg·g−1 ww protein) (p < 0.05) (Fig. 2), whereas MT concentrations in Palaemon elegans were approximately 2.5-fold higher than in Palaemonetes varians (P < 0.05) (4.34 ± 0.99 mg·g−1 ww protein and 1.65 ± 0.39 mg·g−1 ww protein, respectively) (Fig. 2) and were not significantly different from M. fortunata. These results do not support the theory that MT concentrations are directly related to the environment where the shrimps were collected. Thus, MT concentrations followed the order: R. exoculata > P. elegans > M. fortunata = P. varians. Nevertheless, the higher MT levels in R. exoculata suggest that this shrimp species is more exposed to metal-contamination.

image

Figure 2.  Metallothionein concentrations (MT) in the edible tissues of hydrothermal (Rimicaris exoculata and Mirocaris fortunata) and coastal shrimp (Palaemon elegans and Palaemonetes varians). The data represent average ± standard deviation (SD), n = 16. Values followed by the same letter are not statistically different (p > 0.05).

Download figure to PowerPoint

Regarding antioxidant enzymes activities, all the results obtained, except the ones for cytosolic CAT activity, show a negative relationship with MT levels, (MT = −0.345 SOD + 6.2, r = 0.728, P < 0.05; MT = −175.0 total GPx + 7.5, r = 0.858, P < 0.05; MT = −1344.8 Se-GPx + 11.8, r = 0.911, P < 0.05). The cytosolic SOD activity was significantly different among all sampled shrimp species (ANOVA, F3,30 = 55.89, P < 0.001). Cytosolic SOD activity was significantly higher in M. fortunata from Rainbow (1615.99 ± 5.66 U mg−1 protein) compared with the other vent and coastal species (p < 0.05). At the same time, the hydrothermal vent shrimp R. exoculata exhibited the lowest SOD activity (2.56 ± 0.66 U mg−1 protein) (Fig. 3A). No significant differences in the activity of cytosolic SOD were found between the two coastal shrimp species, P. elegans and P. varians, from the Ria Formosa Lagoon (P > 0.05) (5.14 ± 1.58 and 5.67 ± 1.73 U mg−1 protein, respectively) (Fig. 3A).

image

Figure 3.  Antioxidant enzymes activities of (A) cytosolic superoxide dismutase; (B) cytosolic catalase; (C) Total glutathione peroxidase and (D) selenium-dependent glutathione peroxidase in edible tissues of hydrothermal (Rimicaris exoculata and Mirocaris fortunata) and coastal shrimp (Palaemon elegans and Palaemonetes varians). The data represent average and ± standard deviation (SD) for n = 16. Values followed by the same letter are not statistically different (p > 0.05).

Download figure to PowerPoint

All shrimp species had significantly different cytosolic CAT activity (ANOVA, F3,26 = 28.60, P < 0.001). The activity of cytosolic CAT was approximately threefold higher in the two vent shrimp species (0.0042 ± 0.0005 mmoles min−1 mg−1 protein for R. exoculata and 0.0048 ± 0.001 mmoles min−1 mg−1 protein for M. fortunata) compared with their coastal counterparts (0.0014 ± 0.0005 mmoles min−1 mg−1 protein for P. elegans and 0.002 ± 0.0005 mmoles min−1 mg−1 protein for P. varians) (P > 0.05) (Fig. 3B). Each and every analysed shrimp species was significantly different for total GPx activity (ANOVA, F3,26 = 18.47, P < 0.001). The antioxidant enzyme levels followed a similar pattern of cytosolic SOD, where a significantly higher activity was observed in M. fortunata (0.040 ± 0.01 μmoles min−1 mg−1 protein) compared with all the other shrimp species (p < 0.05) (Fig. 3C). As occurred for SOD and CAT activities, no significant differences were observed in total GPx between coastal shrimp P. elegans (0.023 ± 0.004 μmoles min−1 mg−1 protein) and P. varians (0.015 ± 0.007 μmoles min−1 mg−1 protein) collected in the Ria Formosa Lagoon (p > 0.05). Moreover, the hydrothermal vent shrimp R. exoculata exhibited no significant differences compared with P. varians (P > 0.05) (Fig. 3C). As occurred for all above antioxidant enzymes, Se-GPx activity was significantly different for all shrimp species (ANOVA, F3,27 = 4.32, P < 0.01). This enzyme activity represents approximately one third of the total GPx activity in both hydrothermal and coastal shrimp species (Fig. 3D). No significant differences were found in GPx activities between the hydrothermal shrimp M. fortunata (0.007 ± 0.001 μmoles min−1 mg−1 protein) and both coastal species from Ria Formosa (p > 0.05). On the other hand, Se-GPx activity in R. exoculata (0.003 ± 0.001 min−1 mg−1 protein) was approximately half of that observed for the other vent and coastal species (p < 0.05) (Fig. 3D).

As occurred for MT levels, no direct relationships were found in antioxidant enzyme activities between the two shrimp species from Rainbow site; however, their coastal counterparts do not show significant differences between them. Direct correlation with environment was only found in cytosolic CAT activity, but there were no significant differences between shrimp species within hydrothermal vent and coastal environments.

Discussion

  1. Top of page
  2. Abstract
  3. Problem
  4. Material and Methods
  5. Results
  6. Discussion
  7. Summary
  8. Acknowledgements
  9. References

An intriguing vent paradox is how to reconcile the fast growth rates and abundant biomass that typify vent species with the highly toxic and stressful nature of their deep-sea environment (Dixon et al. 2000). This is particularly evident at the Rainbow hydrothermal vent site, where the highest metal concentrations in MAR hydrothermal area can be found (Douville et al. 1997, 2002; Desbruyères et al. 2000) and caridean shrimp species Rimicaris exoculata and Mirocaris fortunata together with the vent mussel Bathymodiolus azoricus co-dominate the Rainbow hydrothermal vent megafauna.

Metallothioneins have been proposed as a biomarker of metallic exposure in several organisms (Amiard & Cosson 1997). Amiard et al. (2006) recently compiled several studies showing a clear correlation between metallic concentrations with MT levels, and an evident induction of this protein after Cd, Cu and Zn exposures in aquatic invertebrates, including decapod shrimps. Crustacean species are widely used as biological indicators of environmental alterations, as they play a key ecological role as planktivorous grazers, epibenthic scavengers or as prey species (Clark 1989). Generally, these studies are focussed mainly on the hepatopancreas tissue as it has a central role in the metabolism, storage and detoxification of metals (Pourang et al. 2004). In the present work, however, we considered the whole soft tissue due to technical constraints for antioxidant enzyme determination.

As antioxidant enzymes can also protect against metal-induced reactive oxygen species, it is important to understand both MT and antioxidant enzymatic responses in these organisms. Therefore, this study was the first attempt to compare MT levels and antioxidant defence systems in four shrimp species from hydrothermal vent and coastal environments and try to explain the importance of such responses in the resistance and tolerance of these species to a metal-rich environment.

Considering the possible influence of the environment in MT concentrations, the results obtained showed that MT levels were markedly different between shrimp species from each vent and coastal site. We expected a higher similarity in MT concentrations between shrimp from the same type of environment, as the Rainbow shrimp exhibited higher metal concentration levels in their fluids and in whole body tissue burden (Kádár et al. 2006 obtained for Rimicaris: 35.6 × 103 μg·g−1 dry weight Fe, 1.8 × 103 μg·g−1 dry weight Zn, 0.8 × 103 μg·g−1 dry weight Cu and for Mirocaris: 6.6 × 103 μg·g−1 dry weight Fe, 2.5 × 103 μg·g−1 dry weight Zn, 1.0 × 103 μg·g−1 dry weight Cu) when compared with the coastal species collected in the Ria Formosa Lagoon (data not shown). However, this was only true for R. exoculata, while the other vent shrimp, M. fortunata, had MT concentrations similar to those found for the coastal species Palaemon elegans. Although M. fortunata are found more distant from active venting than R. exoculata, and therefore have a lower exposure to the vent fluids, they seem to accumulate more metals in their tissues, which may suggest more efficient detoxification strategies to this potentially toxic environment (Kádár et al. 2006).

Therefore, the differences observed in MT levels between vent and coastal shrimp can derive from inter-specific differences in the basal levels of these proteins, rather than reflecting a metabolic response to their environments. Geret et al. 2002 found similar MT levels in R. exoculata from Rainbow hydrothermal field. However, no information concerning the basal MT levels in M. fortunata, P. elegans and Palaemonetes varians is available. Also, in crustaceans a relatively high amount of metals is associated with the insoluble forms (Geret et al. 2002) that can be mobilized and immobilized during the moult cycle (Engel & Brouwer 1991, 1993). In hydrothermal vent shrimp, intra-specific adaptations to deep-sea hydrothermal conditions can also derive from their different nutritional behaviours, i.e. M. fortunata has been described as an opportunistic scavenger while R. exoculata possess symbiotic bacteria in their branchial chambers (Gebruk et al. 2000). Nevertheless, we can also hypothesize that, although coastal shrimp exhibit the same sampling environment and analogous feeding habits, vent shrimp have different microhabitats (described earlier). Unfortunately no available data concerning metal concentration levels in the surrounding water of each microhabitat were found in the literature to confirm this assumption.

In general, the antioxidant enzyme activities in the two hydrothermal shrimp species are significantly lower than those found for the mussel B. azoricus from the same hydrothermal vent site, except the cytosolic SOD activity (5.52 ± 1.08 U·mg−1 protein), which was the same order of magnitude (Bebianno et al. 2005). Hydrothermal vent mussel species B. azoricus at Rainbow site exhibit much higher cytosolic CAT, total GPx and Se-GPx activities. However, cytosolic SOD activity (5.52 ± 1.08 U·mg−1 protein) seems to be in agreement with that obtained in shrimp species, although being closer to coastal shrimp species rather than hydrothermal vent shrimp species.

Concerning the relationship between MT levels and antioxidant enzymes, results point out that in general, antioxidant enzyme activities (especially cytosolic SOD, Total GPx and Se-GPx) in both vent and coastal shrimp species had an inverse pattern compared with the MT levels, suggesting a negative relationship between these two protection systems. However, this negative relationship is more noticeable among vent shrimp species. Although antioxidant enzymes are the main factor responsible for ROS detoxification inside the cells, the antioxidant properties of MT have also been described, mainly in the elimination of the hydroxyl radical (Chubatsu & Meneghini 1993). This suggests that when MT levels in vent and coastal shrimp are enhanced, they are more efficiently sequestered from the intracellular medium. Consequently, metal-induced reactive oxygen species are less likely to be formed when MT synthesis increases, leading to a natural decrease in the antioxidant enzymatic protections.

Even so, the biochemical responses towards metals in coastal shrimp are more similar between them, than between hydrothermal vent shrimp. Thus, microhabitat and feeding habitats are the crucial variables for metal uptake and consequently will influence the metal detoxification systems.

Summary

  1. Top of page
  2. Abstract
  3. Problem
  4. Material and Methods
  5. Results
  6. Discussion
  7. Summary
  8. Acknowledgements
  9. References

Very few studies deal with the specific biochemical responses from hydrothermal vent organisms as an adaptation to their extreme environment. Shrimp are key species in these environments as they dominate the hydrothermal vent fauna along with hydrothermal vent mussels of the genus Bathymodiolus. Results obtained suggest that biochemical responses in vent and coastal shrimp are not only affected by environmental characteristics but also by interspecific differences. The detoxification strategies towards metals (MT and antioxidant enzymes) observed in several shrimp species suggest distinct metabolic responses; nevertheless these responses confer successful adaptations to survival in a metal-extreme environment.

Acknowledgements

  1. Top of page
  2. Abstract
  3. Problem
  4. Material and Methods
  5. Results
  6. Discussion
  7. Summary
  8. Acknowledgements
  9. References

This study was largely funded by the SEAHMA Project (Seafloor and Sub-Seafloor Hydrothermal Modelling in the Azores Sea; PDCTM/P/MAR/15281/1999) and the crew of N/O L'Atalante and Victor 6000 (IFREMER). A Serafim and R. Company were supported by FCT grants (SFRH/BPD/8407/2002 and SFRH/BD/904/2000, respectively) of the Ministry of Science and Technology of Portugal.

References

  1. Top of page
  2. Abstract
  3. Problem
  4. Material and Methods
  5. Results
  6. Discussion
  7. Summary
  8. Acknowledgements
  9. References
  • Amiard J.C., Cosson R.P. (1997) Les métallothionéines. In: LagadicL., CaquetT., AmiardJ.C., RamadeF. (Eds), Biomarqueurs en écotoxicologie. Aspects Fondamentaux Masson, Paris: 5366.
  • Amiard J.C., Amiard-Triquet C., Barka S., Pellerin J., Rainbow P.S. (2006) Review: metallothioneins in aquatic invertebrates: their role in metal detoxification and their use as biomarkers. Aquatic Toxicology, 76, 160202.
  • Bebianno M.J. (1995) Effects of pollutants in the Ria Formosa Lagoon, Portugal. The Science of the Total Environment, 171(1–3), 107115.
  • Bebianno M.J., Langston W.J. (1989) Quantification of metallothioneins in marine invertebrates using differential pulse polarography. Portugaliae Electrochimica Acta, 7, 5964.
  • Bebianno M.J., Company R.M., Serafim A.M., Camus L., Cosson R., Fiala-Medioni A. (2005) Antioxidant systems and lipid peroxidation in Bathymodiolus azoricus from Mid-Atlantic Ridge hydrothermal vent fields. Aquatic Toxicology, 75(4), 354373.
  • Blum J., Fridovich I. (1984) Enzymatic defences against oxygen toxicity in the hydrothermal vent animals Riftia pachyptila and Calyptogena magnifica. Archives of Biochemistry and Biophysics, 228(2), 617629.
  • Caetano M., Falcão M., Vale C., Bebianno M.J. (1997) Tidal flushing of ammonium, iron and manganese from inter-tidal sediment pore waters. Marine Chemistry, 58, 203211.
  • Caetano M., Vale C., Bebianno M.J. (2002) Distribution of Fe, Mn, Cu and Cd in Upper Sediments and Sediment-Trap Material of Ria Formosa (Portugal). Journal of Coastal Research, 36, 118123.
  • Casanova B., Brunet M., Segonzac M. (1993) L'Impact d'une épibiose bactérienne sur la morphologie fonctionnelle de crevettes associées à l'hydrothermalisme médio-atlantique. Cahier de Biologie Marine, 34, 573588.
  • Chubatsu L.S., Meneghini R. (1993) Metallothionein protects DNA form oxidative damage. The Biochemical Journal, 291, 193198.
  • Clark R.B. (1989) Marine Pollution. Oxford University Press, Oxford.
  • Darley-Usmar V., Wiseman H., Halliwell B. (1995) Nitric oxide and oxygen radicals: a question of balance. FEBS letters, 369, 131135.
  • Desbruyères D., Segonzac M. (1997) Handbook of Deep-sea Hydrothermal Vent Fauna. IFREMER, Brest.
  • Desbruyères D., Almeida A., Biscoito M., Comtet T., Khripounoff A., Le Bris N., Sarradin P.M., Segonzac M. (2000) A review of the distribution of hydrothermal vent communities along northern mid-Atlantic Ridge: dispersal vs. environment controls. Hydrobiologia, 440, 201216.
  • Desbruyères D., Biscoito M., Caprais J.C., Colço A., Comtet T., Crassous P., Fouquet Y., Khripounoff A., Le Bris N., Olu K., Riso R., Sarradin P.M., Segonzac M., Vangriesheim A. (2001) Variations in deep-see hydrothermal vent communities on Mid-Atlantic Ridge near Azores plateau. Deep-Sea Research 48, 13251346.
  • Dixon D.R., Wilson J.T., Dixon L.R. (2000) Toxic vents and DNA damage. InterRidge News, 9(1), 1314.
  • Douville E., Charlou J.L., Donval J.P., Knoery J., Fouquet Y., Bienvenu P., Appriou P. (1997) Trace elements in fluids from the new Rainbow hydrothermal field (36°14’ N, MAR): a comparison with other Mid-Atlantic Ridge fluids. EOS Transactions American Geophysical Union, 78(46), 832.
  • Douville E., Bienvenu P., Charlou J.L., Donval J.P., Fouquet Y., Appriou P., Gamo T. (1999) Yttrium and rare earth elements in fluids from various deep-sea hydrothermal systems. Geochimica et Cosmochimica Acta, 63, 627643.
  • Douville E., Charlou J.L., Oelkers E.H., Bienvenu P., Jove Colon C.F., Donval J.P., Fouquet Y., Prieur D., Appriou P. (2002) The rainbow vent fluids (36°14’ N, MAR): the influence of ultramafic rocks and phase separation on trace metal content in Mid-Atlantic Ridge hydrothermal fluids. Chemical Geology, 184, 3748.
  • Engel D.W., Brouwer M. (1991) Short-term metallothionein and copper changes in blue crab at ecdysis. Biological Bulletin, 180, 447452.
  • Engel D.W., Brouwer M. (1993) Crustacean as models for metal metabolism: I. Effects of the molt cycle on blue crab metal metabolism and metallothionein. Marine Environmental Research, 35, 15.
  • FAO – Food and Agriculture Organization of the United Nations (1980) FAO Species Catalogue. Vol. 1 – Shrimps and prawns of the world. An Annotated Catalogue of Species of Interest to Fisheries, Rome.
  • Fouquet Y., Charlou J.L., Ondréas H., Radford-Knoery J., Donval J.P., Douville E., Aprioual R., Cambon P., Pell H., Landur J.Y., Normand A. (1997) Discovery and first submersible investigation on the Rainbow hydrothermal field on the MAR (36°14 N). EOS Transactions American Geophysical Union, 78(46), 832.
  • Fridovich I. (1998) Oxygen toxicity: a radical explanation. The Journal of Experimental Biology, 201, 12031209.
  • Gebruk A.V., Pimenov N.V., Savvichev A.S. (1993) Feeding specialization of bresiliid shrimps in the TAG site hydrothermal community. Marine Ecology Progress Series, 98, 247253.
  • Gebruk A.V., Southward E.C., Kennedy H., Southward A.J. (2000) Food sources, behaviour, and distribution of hydrothermal vent shrimps at the Mid-Atlantic Ridge. Journal of the Marine Biological Association of the United Kingdom, 80, 485499.
  • Geret F., Riso R., Sarradin P.M., Caprais J.C., Cosson R. (2002) Metal bioaccumulation and storage forms in the shrimp Rimicaris exoculata, from the Rainbow hydrothermal field (Mid-Atlantic Ridge), preliminary approach to the fluid-organism relationship. Cahier de Biologie Marine, 43, 4352.
  • Greenwald R.A. (1985) Handbook of Methods for Oxygen Radical Research. CRC Press, Boca Raton, FL, USA.
  • Instituto Hidrográfico (1998) Contribuição para Instituto Hidrográfico para a elaboração do capítulo 4 do Relatório de Estado da Qualidade da Região IV da Comissão de Oslo e Paris. Setembro, Lisboa: 21 pp.
  • Kádár E., Costa V., Santos R. S. (2006) Distribution of micro-essential (Fe, Cu, Zn) and toxic (Hg) metals in tissues of two nutritionally distinct hydrothermal shrimps. Science of the Total Environment, 358, 143150.
  • Langston W.J, Bebianno M.J., Burt G.R. (1998) Metal handling strategies in molluscs. In: LangstonW.J., BebiannoM.J (eds), Metal Metabolism in Aquatic Environments. Chapman & Hall, London: 219283.
  • Lawrence R.A., Burk R.F. (1976) Glutathione peroxidase activity in selenium-deficient rat liver. Biochemical and Biophysical Research Communications, 71, 952958.
  • Lemaire P. & Livingstone D.R. (1993) Pro-oxidant/antioxidant processes and organic xenobiotic interactions in marine organisms in particular the flounder Platichthys flesus and the mussel Mytilus edulis. Trends Comparative Biochemistry and Physiology, I, 11191150.
  • Livingstone D.R. (2001) Contaminated-stimulated reactive oxygen species production and oxidative damage in aquatic organisms. Marine Pollution Bulletin, 42, 656666.
  • Lowell R.P., Rona P.A., von Herzen R.P. (1995) Seafloor hydrothermal systems. Journal of Geophysical Research, 100, 327352.
  • Lowry O.H., Rosenbrough N.J., Farr A.L., Randall R.J. (1951) Protein measurement with the Folin phenol reagent. Journal of Biological Chemistry, 193, 265275.
  • Martin, J. W., Christiansen, J. C. (1995) A new species of the shrimp genus Chorocaris Martin and Hessler 1990 from hydrothermal vents along the Mid-Atlantic Ridge. Proceedings of the Biological Society of Washington, 108, 220227.
  • McCord J.M., Fridovich I. (1969) Superoxide dismutase: an enzymatic function for erythrocuprein (hemocuprein). Journal of Biological Chemistry, 244(22), 60496055.
  • Park J.D., Liu Y., Klaassen C.D. (2001) Protective effect of metallothionein against the toxicity of cadmium and other metals. Toxicology, 163, 93100.
  • Polz M.F., Robinson J.J., Cavanaugh C.M., van Dover C.L. (1998) Trophic ecology of massive shrimp aggregations at a Mid-Atlantic Ridge hydrothermal vent site. Limnology and Oceanography, 43, 16311638.
  • Pourang N., Dennis J.H., Ghourchian H. (2004) Tissue distribution and redistribution of trace elements in shrimp species with the emphasis on the roles of metallothionein. Ecotoxicology, 13, 519533.
  • Pruski A.M, Dixon D.R. (2003) Toxic vents and DNA damage: first evidence from a naturally contaminated deep-sea environment. Aquatic Toxicology, 64, 113.
  • Renninger G.H., Kass L., Gleeson A., van Dover C.L., Battelle B.A., Jinks R.N., Herzog E.D., Chamberlain S.C. (1995) Sulfide as a chemical stimulus for deep-sea hydrothermal vent shrimp. Biology Bulletin, 189, 6976.
  • Santos R., Silva J., Alexandre A., Navarro N., Barrón C., Duarte C.M. (2004) Ecosystem metabolism and carbon fluxes of a tidally-dominated coastal lagoon. Estuaries, 27 (6), 977985.
  • Sarradin P.M., Caprais J.C., Briand P., Gail F., Shillito B., Desbruères D. (1998) Chemical and thermal description of the environment of the Genesis hydrothermal vent community (13°N, EPR). Cahier de Biologie Maritime de Roscoff, 38, 159167.
  • Segonzac M., de Saint Laurent M., Casanova B. (1993) L’énigme du comportement trophique des crevettes Alvinocarididae des sites hydrothermaux de la dorsale médio-atlantique. Cahier de Biologie Marine, 34, 535571.
  • Von Damm K.L. (1990) Seafloor hydrothermal activity: black smoker chemistry and chimneys. Annual Review of Earth and Planetary Sciences, 18, 173204.
  • Von Damm K.L. (1992) Short-term Variability, Phase Separation and Water-rock Reaction in Hydrothermal Fluids from 9–10°N, East Pacific Rise. In: KharakaY., MaestA. (Eds). Proceedings of the 7th International Symposium on Water-Rock Interaction A.A. Balkema Publishers, Park City, UT: 16791680.
  • Von Damm K.L., Oosting S.E., Kozlowski R., Buttermore L.G., Colodner D.C., Edmonds H.N., Edmond J.M., Grebmeier J.M. (1995) Evolution of East Pacific Rise hydrothermal vent fluids following a volcanic eruption. Nature, 375, 4750.
  • William A.B., Rona P.A. (1986) Two new Caridean shrimps (Bresiliidae) from hydrothermal field on the Mid-Atlantic Ridge. Journal of Crustacean Biology, 6, 446462.
  • Winston G.W., Di Giulio R.T. (1991) Prooxidant and antioxidant mechanisms in aquatic organisms. Aquatic Toxicology, 19, 137161.