Abstract

Aquatic environments are especially susceptible to anthropogenic chemical pollution. Yet although knowledge on the biological effects of pollutants on aquatic organisms is increasing, far less is known about how ecologically-important interspecific interactions are affected by chemicals. In particular, the consequences of anthropogenic pollution for the interaction of hosts and parasites are poorly understood. Here, we examine how exposure to 17β-oestradiol (E2)—a natural oestrogen and a model endocrine disrupting chemical (EDC) —affects infection susceptibility and emergent infection phenotypes in an experimental host–parasite system; three spined sticklebacks (Gasterosteus aculeatus) infected with the common, debilitating cestode Schistocephalus solidus. We exposed individual sticklebacks to a 0ngl−1 (control), 10ngl−1 or 100ngl−1 E2 treatment before feeding them infective stages of S. solidus. E2 exposure significantly elevated vitellogenin (VTG) levels—a biomarker of exposure to xenoestrogens—in both female and male fish, and reduced their body condition. Susceptibility to parasite infection was unaffected by EDC exposure; however, E2 treatment and fish sex interacted significantly to determine the growth rate of parasites, which grew quickest in male hosts held under the higher (100ngl−1) E2 treatment. Tissue VTG levels and parasite mass correlated positively across the whole sample of experimentally infected fish, but separate regressions run on the male and female datasets demonstrated a significant relationship only among male fish. Hence, among males—but not females—elevated VTG levels elicited by E2 exposure led to more rapid parasite growth. We outline plausible physiological mechanisms that could explain these results. Our results demonstrate that oestrogenic pollutants can alter host–parasite interactions by promoting parasite growth, and that male hosts may be disproportionately affected. Because ecologically-relevant effects of infection on host antipredator responses, growth, energetics and reproductive development all depend on parasite mass in this host–parasite system, our results indicate that EDCs can mediate the ecological consequences of infections. We therefore consider the implications of our results for the ecology of hosts and parasites in polluted environments.

Highlights

  • Human activities are rapidly changing the conditions that wildlife experience in nature (Candolin and Wong, 2012; Dubinsky and Stambler, 1996; Harvell et al, 2002)

  • The development of infections was not associated with E2 treatment or fish sex

  • There was no main effect of infection status on fish body condition factor (K) at the end of the study; K was significantly affected by both fish sex and by E2 treatment, with females having higher K values than males, and with K being reduced with increasing E2 dose

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Summary

Introduction

Human activities are rapidly changing the conditions that wildlife experience in nature (Candolin and Wong, 2012; Dubinsky and Stambler, 1996; Harvell et al, 2002). Organisms already encountering a range of natural environmental stressors, including predators, parasites and competitors, are faced with a broad array of anthropogenic stressors. The effects of individual natural and anthropogenic stressors are typically studied in isolation, with test organisms otherwise experiencing ideal conditions (Holmstrup et al, 2010; Sures, 2008). Environmental stressors have considerable capacity to interact and produce additive, synergistic or antagonistic effects (Brian et al, 2005; Kiesecker, 2002; Marcogliese et al, 2010), and understanding how multiple stressors interact to influence animal health in anthropogenically disturbed ecosystems represents a key challenge (Marcogliese and Pietrock, 2011; Sih et al, 2004). Since fish are likely to encounter both parasites and chemical pollutants in their natural environments, they represent ideal vertebrate models for studying interactions between anthropogenic and natural stressors

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