Oxidative stress in native and invasive crustaceans related with pollution and parasitism in a warming scenario Aquatic organisms are exposed to multiple natural and anthropogenic stressors, including pollution, parasites, invasive species and climate change. These factors interact in a diversity of ways. However few studies consider realistic ecological contexts taking into account the synergy between these factors on aquatic biota. Increasing interest has been devoted to the interactions between parasitism and pollution in aquatic ecosystems [1], but there are major gaps in knowledge of how these stressors affect animal health [2]. For example, what are the physiological mechanisms underlying the response of aquatic organisms to pollution and concurrent parasite infection? Additional complexity is added by the effect of climate change which can interact with both pollutants and parasites [3,4]. Furthermore, these stressors are expected to affect differently the physiology of native and invasive species; invasive species are likely to have a wider range of environmental tolerance [5]. The mechanisms of pollution-, parasitism- and temperature-induced health effects involve oxidative stress [2,6,7]. Different enzymatic antioxidant mechanisms such as superoxide dismutase (SOD), glutathione peroxidase (GPx) and catalase (CAT), as well as non-enzymatic components (glutathione, carotenoids, ascorbate, etc), are used to protect cells against oxidative stress in both vertebrates and invertebrates [7]. However, when control mechanisms are insufficient, reactive oxygen species (ROS) can induce damage at different levels. The evaluation of antioxidant defense mechanisms in aquatic organisms is a useful measure of the capacity of detoxification from ROS caused by the combined effect of endogenous (parasites) and environmental (pollution and climate change) factors. Brine shrimps Artemia spp. (Anostraca) are keystone organisms and essential link in hypersaline coastal and inland systems around the world [8]; they are also an invaluable resource in aquaculture worlwide [9]. Owing to their ability to bioaccumulate pollutants, their wide geographic distribution, the availability of dried cysts, the ease of laboratory culture and maintenance, their short life-cycle and high fecundity, Artemia have become one of the most important test organisms for applied toxicology [10]. An excellent model system to study interactions between pollutants and parasites is the highly parasitized Artemia parthenogenetica (hereafter AP) population from the Odiel and Tinto estuary, one of the most polluted estuarine systems in Europe [11]. AP from Odiel has extraordinarily high levels of cestode infection, mainly Flamingolepis liguloides and Confluaria podicipina [12]. Both parasites induce strong physiological and behavioural changes in Artemia [13,14] likely to affect its response to pollution. Moreover this is one of the last native Artemia populations in the Iberian Peninsula, most of which have been displaced by the American congener A. franciscana (hereafter AF) [15]. This provides an exceptional opportunity to test for physiological mechanisms explaining invasion resistance by comparing biomarkers of oxidative stress with AP and AF populations from relatively unpolluted environments. BIBLIOGRAPHY [1] Sures B (2008) Environmental parasitology. Interactions between parasites and pollutants in the aquatic environment. Xth EMOP, August 2008. Parasite 15, 434–438 [2] Marcogliese DJ, Brambilla LG, Gagné F, Gendron AD (2005) Joint effects of parasitism and pollution on oxidative stress biomarkers in yellow perch Perca flavescens. 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Ecological Indicators 23: 274-279 [7] Nunes B, Carvalho F, Guilhermino L (2006) Effects of widely used pharmaceuticals and a detergent on oxidative stress biomarkers of the crustacean Artemia parthenogenetica. Chemosphere 62 (4): 581-94 [8] Sánchez MI, Varo N, Green AJ, Ramos C, Amat J (2013)Cestodes change the isotopic signature of brine shrimp hosts: implications for aquatic food webs. Int. J. Parasitol 43(1):73-80 [9] Sorgeloos P, Dhert P, Candreva P (2001) Use of the brine shrimp, Artemia spp., in marine fish larviculture. Aquaculture 200: 147–159 [10] Nunes BS, Carvalho FD, Guilhermino LM, Van Stappen G (2006) Use of the genus Artemia in ecotoxicity testing. Environ Pollut. Nov;144(2):453-62. [11] Grande JA, Borrego J, Morales JA (2000) A study of heavy metal pollution in the Tinto-Odiel estuary in Southwestern Spain using factor analysis. Environmental Geology 39: 1095-1101 [12] Sánchez MI, Nikolov PN, Georgieva DD, Georgiev BB, Vasileva G, Pankov P, Paracuellos M, Lafferty K, Green AJ (2013) High prevalence and abundance of cestode parasites throughout the annual cycle of Artemia salina and A. parthenogenetica in coastal Spain: relationship with abundance of avian final hosts. Journal of Parasitology 112(5):1913-23 [13] Sánchez MI, Thomas F, Perrot-Minnot MJ, Bertrand-Michel J, Missé D (2009) Neurological and physiological disorders in Artemia harboring manipulative cestodes. Journal of Parasitology 95 (1): 20-24 [14] Sánchez MI, Georgiev BB, Green AJ (2007) Avian cestodes affect the behaviour of their intermediate host Artemia parthenogenetica: an experimental study. Behavioural Processes 74: 293-299 [15] Amat F, F Hontoria, O Ruiz, AJ Green, MI Sanchez, J Figuerola, F Hortas (2005) The American brine shrimp as an exotic invasive species in the western Mediterranean. Biological Invasions 7: 37-47
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