Abstract
Amphipods are commonly parasitized by acanthocephalans and microsporidians and co-infections are found frequently. Both groups of parasites are known to have severe effects on their host. For example, microsporidians can modify host sex ratio and acanthocephalans can manipulate the behavior of the amphipod to promote transmission to the final host. These effects influence host metabolism in general and will also affect the ability of amphipods to cope with additional stressors such as environmental pollution, e.g., by toxic metals. Here we tested the effects of sub-lethal concentrations of cadmium on glycogen and lipid levels, as well as on the 70kDa heat shock protein (hsp70) response of field collected Gammarus fossarum, which were naturally infected with microsporidians and the acanthocephalan Polymorphus minutus. Infected and uninfected G. fossarum were exposed to a nominal Cd concentration of 4 µg/L, which resembled measured aqueous Cd concentration of 2.9 µg/L in reconstituted water for 7 d at 15 °C in parallel to an unexposed control. After exposure gammarids were snap frozen, weighed, sexed and tested for microsporidian infection by PCR. Only individuals containing the microsporidian Dictyocoela duebenum were used for the further biochemical and metal analyses. P. minutus infected amphipods were significantly smaller than their uninfected conspecifics. Mortality was insignificantly increased due to cadmium exposure, but not due to parasite infection. Microsporidian infection in combination with cadmium exposure led to increased glycogen levels in female gammarids. An increase of glycogen was also found due to interaction of acanthocephalan and microsporidian infection. Elevated lipid levels were observed in all groups infected with microsporidians, while acanthocephalans had the opposite effect. A positive correlation of lipid and glycogen levels was observed. The general stress response measured in form of hsp70 was significantly increased in microsporidian infected gammarids exposed to cadmium. P. minutus did not affect the stress response of its host. Lipid levels were correlated negatively with hsp70 response, and indicated a possible increased stress susceptibility of individuals with depleted energy reserves. The results of our study clearly demonstrate the importance of parasitic infections, especially of microsporidians, for ecotoxicological research.
Highlights
Parasites are natural and ubiquitous parts of ecosystems and their role for ecosystem function and stability has been recognized in recent years (Marcogliese, 2005; Hudson, Dobson & Lafferty, 2006; Kuris et al, 2008)
Sampling of gammarids and exposure design Gammarids were collected by kick-sampling from a small stream (Rumbach) near Mulheim (N51◦25′28.628′; E6◦54′25.553′′), NRW, Germany in March 2014. This site is characterized by a mixed population of Gammarus pulex and Gammarus fossarum, and high prevalence of the acanthocephalan Polymorphus minutus in both amphipod species
The gammarids were grouped by acanthocephalan infection and kept in the laboratory for 2 days at 15 ◦C in reconstituted water (7.36 μM NaCl, 231.39 μM KCl, 117.13 μM NaHCO3, 707.05 μM, MgSO4 · 7H2O, 303.70 μM)
Summary
Parasites are natural and ubiquitous parts of ecosystems and their role for ecosystem function and stability has been recognized in recent years (Marcogliese, 2005; Hudson, Dobson & Lafferty, 2006; Kuris et al, 2008). Parasites are often neglected in ecotoxicological research, results of recent studies showed that they may influence the host response to pollution (Sures, 2004; Sures, 2008a; Sures, 2008b; Marcogliese & Giamberini, 2013) and can impact the stress response of their host, especially on the biochemical level (Sures, Lutz & Kloas, 2006; Sures & Radszuweit, 2007; Frank et al, 2011; Frank et al, 2013; Gismondi, Cossu-Leguille & Beisel, 2012a; Gismondi et al, 2012a; Gismondi et al, 2012b; Filipovic Marijic, Vardic Smrzlic & Raspor, 2013; Grabner, Schertzinger & Sures, 2014) Such impacts are relevant when using stress responses on the biochemical level as biomarkers in environmental monitoring programs to indicate the presence of contaminants and to unravel their effects on organisms. Amphipods are affected by several parasite groups including acanthocephalans and microsporidians (Taraschewski, 2000; Stentiford et al, 2013)
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