Aquatic Toxicology 103 (2011) 222–224 Contents lists available at ScienceDirect Aquatic Toxicology journal homepage: www.elsevier.com/locate/aquatox Immune suppression of the echinoderm Asterias rubens (L.) following long-term ocean acidification Bodil Hernroth a,b,∗ , Susanne Baden c , Mike Thorndyke a , Sam Dupont c a b c The Royal Swedish Academy of Sciences, The Sven Lovén Centre for Marine Sciences, Kristineberg 566, 450 34 Fiskebäckskil, Sweden Department of Biomedicine, Kristianstad University, 291 88 Kristianstad, Sweden Department of Marine Ecology, University of Gothenburg, The Sven Lovén Centre for Marine Sciences, Kristineberg 566, 450 34 Fiskebäckskil, Sweden a r t i c l e i n f o Article history: Received 26 February 2011 Accepted 1 March 2011 Keywords: Ocean acidification CO2 Immunity Stress indicators Marine invertebrates a b s t r a c t We compared effects of exposure to predict near-future (2100) ocean acidification (OA; pH 7.7) and normal seawater (Control; pH 8.1) on immune and stress responses in the adult sea star Asterias rubens. Analyses were made after one week and after six months of continuous exposure. Following one week exposure to acidified water, the pH of coelomic fluid was significantly reduced. Levels of the chaperon Hsp70 were elevated while key cellular players in immunity, coelomocytes, were reduced by approximately 50%. Following long-term exposure (six months) levels of Hsp70 returned to control values, whereas immunity was further impaired, evidenced by the reduced phagocytic capacity of coelomocytes and inhibited activation of p38 MAP-kinase. Such impacts of reduced seawater pH may have serious consequences for resistance to pathogens in a future acidified ocean. © 2011 Elsevier B.V. All rights reserved. The rise in global atmospheric levels of CO2 not only warms the Earth and destabilizes weather systems, but also dissolves easily into the oceans changing the chemistry of seawater. From the preindustrial era until 2005, the average pH of ocean surface water decreased by 0.1 pH units, representing an increase in the concentration of hydrogen ions of about 30%. A further decrease in pH of about 0.4 units is expected by 2100 based on realistic scenarios for future CO2 emissions (Royal Society, 2005). Calcification impairment of marine biota has been suggested as a potential consequence (Hofmann et al., 2010). However, there is a lack of long term studies on the effects of OA on other vital processes of marine organisms (Dupont et al., 2010) and virtually nothing is known about immune and stress response. In this study we compared immune response of the echinoderm Asterias rubens after long-term (six months) and short-term (one week) exposure to seawater at pH 7.7 [predicted ocean acidification (OA) by the year 2100] with that of sea stars exposed to seawater at pH 8.1 (Controls). Sea stars (n = 6) were kept in 400 L basins (flow-through system, temperature 12 ◦ C, salinity 32‰) and pH was maintained by bubbling CO2 which was regulated and controlled by a computerized system (AquaMedic; Control: pH 8.1, pCO2 = 330.8 ppm, ca = 3.42, ar = 2.17; OA: pH ∗ Corresponding author at: The Royal Swedish Academy of Sciences, SLC Kristineberg 566, 450 34 Fiskebäckskil, Sweden. Tel.: +46 523 18513; fax: +46 523 18502. E-mail addresses: [email protected], [email protected] (B. Hernroth). 0166-445X/$ – see front matter © 2011 Elsevier B.V. All rights reserved. doi:10.1016/j.aquatox.2011.03.001 7.7, pCO2 = 921.6 ppm, ca = 1.51, ar = 0.96). Animals were fed with blue mussels (Mytilus edulis) twice a week until one week of exposure remained, at which point the short-term experiment was initiated with another batch of sea stars (n = 6). At the end of the experiment an arm tip of each sea star was cut and coelomic fluid collected to measure pH (NBS calibrated Methrom pH-meter) and for microscopical determination of the total coelomocyte count. Coelomocytes were harvested through centrifugation and their phagocytic capacity was analyzed (Oweson et al., 2008). Lyzed coelomocytes were prepared both for ELISAanalysis of heat shock protein Hsp-70 (Brun et al., 2008 with the antibody as used by Holm et al., 2008) and for, phosphorylation of mitogen activated protein kinase (MAPK) p38 after challenging coelomocytes with lipopolysaccharide. Data were analyzed using Two-way ANOVA and the post hoc Student–Newman–Keuls method. Tissue carbonate buffers could help to maintain internal pH in the short term, but in sea urchins such compensation has been proven to be incomplete even under moderate environmental hypercapnia (Miles et al., 2007). Accordingly, the present study showed that after only one week of exposure to OA the pH of sea star coelomic fluid was significantly reduced compared to that of controls (Fig. 1A; Diff of mean 0.14; p = 0.008). Similar differences in pH levels were also recorded after six months (Diff of mean 0.16; p = <0.001), indicating that the rate of proton-equivalent ion exchange between the sea stars and ambient seawater was maintained at the same level in both normal and acidified conditions. B. Hernroth et al. / Aquatic Toxicology 103 (2011) 222–224 223 Fig. 1. (A) pH of coelomic fluid was significantly lowered in A. rubens exposed to acidified seawater (OA) compared to that of Controls (C) both after one week (1wk) and six months (6mo) of exposure. (B) Hsp70 increased in coelomocytes of OA treated sea stars after one week of exposure but not after six months compared to that of the controls. (C) Activation of MAPKp38 in LPS challenged coelomocytes was significantly inhibited after six months of OA treatment compared to that after one week and the controls. (D) OA treatment significantly reduced the total coelomocyte counts (TCC) and did so already after one week of exposure. (E) The phagocytic capacity of the coelomocytes decreased in OA-treated sea stars and particularly so after six months of exposure. Letters indicate significant relationship between values. During stress, energy is allocated to maintain protein integrity via the chaperon Hsp70 (Mayer and Bukau, 2005), as well as transferring peptides through the cell thus also affecting immune defense (Moseley, 2000). In echinoderms, enhancement of Hsp70 has been recorded after short term exposure to environmental stressors (Matranga et al., 2002; Oweson et al., 2008) and to physiological stress such as injury and tissue regeneration (Patruno et al., 2001; Holm et al., 2008). In the current study Hsp70 was found to be elevated after one week of OA exposure (Fig. 1B; Diff of means 79.6 abs units per mg protein; p < 0.001) but not after the longterm exposure. It has been suggested that it is too costly for sea stars to over-express Hsp70 in the long-term (Clark et al., 2007) and that lowered pH inhibits transcriptional and/or translational levels (Langenbuch et al., 2006; Todgham and Hofmann, 2009). Another activating pathway of immunity is that of the highly conserved MAPK-p38. The short term exposure to OA did not significantly affect the phosphorylation in LPS triggered coelomo- cytes (Fig. 1C). However, after six months OA had a negative effect with levels of this enzyme reduced by approximately 35% compared to controls (Diff of mean: 3.371, p = 0.049). Such suppression of both Hsp70 and MAPK-p38 caused by long-term exposure to OA may indicate a weakened activation of the immune response. Furthermore, OA-exposed sea stars showed reduced numbers of coelomocytes by approximately 50% after one week (Fig. 1D; Diff of mean 6 × 103 cells per l; p = 0.021) and this reduction remained after six months. Not only was the number of coelomocytes affected, but their phagocytic capacity was also reduced to approximately 30% after six months in acidified seawater (Fig. 1E; Diff of means: 800 phagocytic units, p = 0.001). Thus, only 15% of full phagocytic capacity remained. Such an impairment of phagocytosis after exposure to lowered pH for one month has previously been reported in studies of M. edulis (Bibby et al., 2008). In conclusion, we did not see any lethal effects but identified the likely negative impact of near-future ocean acidification on 224 B. Hernroth et al. / Aquatic Toxicology 103 (2011) 222–224 immunity in the sea star A. rubens. This suggests potential serious consequences for resistance to pathogens in a future acidified sea. Furthermore, our data illustrate the fact that ocean acidification is not solely a calcification issue and highlight the importance of long-term experiments. Acknowledgement This work was supported by Gothenburg University Platform for Integrative Physiology (GRIP; http://www.grip.science.gu.se/). References Bibby, R., Widdicombe, S., Parry, H., Spicer, J., Pipe, R., 2008. Effects of ocean acidification on the immune response of the blue mussel Mytilus edulis. Aquat. Biol. 2, 62–74. Brun, N.T., Bricelj, V.M., MacRae, T.H., Ross, N.W., 2008. Heat shock protein responses in thermally stressed bay scallops, Argopecten irradians, and sea scallops, Placopecten magellanicus. J. Exp. Mar. Biol. Ecol. 358, 151–162. Clark, M.S., Dupont, S., Rosetti, H., Burns, G., Thorndyke, M.C., Peck, L.S., 2007. Delayed arm regeneration in the Antarctic brittle star (Ophionotus victoriae). Aquat. Biol. 1, 45–53. Dupont, S., Ortega-Martínez, O., Thorndyke, M., 2010. Impact of near-future ocean acidification on echinoderms. Ecotoxicology, doi:10.1007/s10646-010-0463-6. Hofmann, G.E., Barrry, J.P., Edmunds, P.J., Gates, R.D., Hutchins, D.A., Klinger, T., Sewell, M.A., 2010. The effect of ocean acidification on calcifying organisms in marine ecosystems: an organism to ecosystem perspective. Annu. Rev. Ecol. Evol. Syst. 41, 127–147. Holm, K., Hernroth, B., Thorndyke, M., 2008. The total numbers of coelomocytes and the expression of HSP70 in wounded sea star during hypoxia. Cell Tissue Res. 334, 319–325. Langenbuch, M., Bock, C., Leibfritz, D., Pörtner, H.O., 2006. Effects of environmental hypercapnia on animal physiology: a 13C-NMR study of protein synthesis rates in the marine invertebrate Sipunculus nudus. Comp. Biochem. Physiol. A 144, 479–484. Matranga, V., Bonaventura, R., Di Bella, G., 2002. HSP70 as a stress marker of sea urchin coelomocytes in short term cultures. Cell. Mol. Biol. 48, 345–359. Mayer, M.P., Bukau, B., 2005. Hsp70 chaperones: cellular functions and molecular mechanism. Cell. Mol. Life Sci. 62, 670–684. Miles, H., Widdicombe, S., Spicer, J.I., Hall-Spencer, J., 2007. Effects of anthropogenic seawater acidification on acid-base balance in the sea urchin Psammechinus miliaris. Mar. Pollut. Bull. 54, 89–96. Moseley, P.L., 2000. Exercise, stress, and the immune conversation. ESSR 28, 128–132. Oweson, C., Sköld, H., Pinsino, A., Matranga, V., Hernroth, B., 2008. Manganese effects on the haematopoietic cells and circulating haemocytes of Asterias rubens (L.). Aquat. Toxicol. 89, 75–81. Patruno, M., Thorndyke, M.C., Candia Carnevali, M.D., Bonasoro, F., Beesley, P.W., 2001. Growth factors, heat-shock proteins and regeneration in echinoderms. J. Exp. Biol. 204, 843–848. Royal Society, 2005. Ocean acidification due to increasing atmospheric carbon dioxide. Policy Document 12/05. The Royal Society, London. Todgham, A., Hofmann, G., 2009. Transcriptomic response of sea urchin larvae Strongylocentrotus purpuratus to CO2 -driven seawater acidification. J. Exp. Biol. 212, 2579–2594.
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