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Ecology of parasitic and micropredatory isopods on coral reefs

Arthropod parasites and micropredators, such as ticks and mosquitoes, influence terrestrial ecosystems and harm their hosts directly and indirectly by vectoring micro-organisms. Whether micropredators similarly affect marine ecosystems and hosts is not well understood. In coral reef fish communities, the most abundant micropredators are isopods, in particular, gnathiids. Our understanding of how isopods affect fishes has been restricted by a lack of information regarding basic isopod biology including; patterns of abundance, parasite identity, host specificity and host pathology. Also it is unknown if small juvenile fish are parasitised by isopods, and if this affects their survival. Sequentially, the aims of my PhD thesis were to understand the ecology of several lesser known parasites in sufficient detail to perform manipulative experiments that could test the effects of micropredation on small juvenile reef fish. All field studies took place at Lizard Island, Great Barrier Reef My first study aimed to describe temporal and spatial patterns of isopod abundance by measuring emergence rates. Gnathiid isopod juveniles emerge from the benthos into the water column to find hosts or change locations. Although diel patterns have been demonstrated, the relationship between substrate and emergence on coral reefs is not clear. I measured emergence rates of parasitic isopods (Gnathiidea and Flabellifera) in 6 “habitats” at 2 very different sites at Lizard Island. Isopods were collected from the periphery and centres of 3 sizes of reef, and from the substrate between these reefs (sand or rubble). At both sites, the most abundant gnathiid species (Gnathia falcipenis and Gnathia sp C), was exclusive to that site. Although strong diel patterns in emergence were observed, gnathiid abundance could not be predicted by habitat. However, gnathiids were larger and more often fed over reef borders than in the centres of reefs. To explain these patterns, I suggested that first stage larvae had the largest influence on total abundance and were patchily distributed in accordance with adults from which they had recently hatched. As later stage larvae also depend on fish, more successful (fed and older larvae) are found on the edges of reefs where appropriate hosts may be more abundant. Gnathiids were over-dispersed in all habitats investigated, including apparently homogeneous beds of coral rubble and sand. This indicated that gnathiid distribution may be better predicted by very fine scale differences in substrate, or that larvae are simply gregarious, and that abundance may be difficult to predict on the basis of substrate. Without reliable differences in parasite abundance among habitats at Lizard Island, subsequent studies would rely on manipulating parasite abundance via excluding wild parasites in the field (which proved very difficult) or by controlling abundance in laboratory simulations. I then investigated host specificity in the 2 most abundant gnathiid species from the previous study. Discrete species distributions between the two sites suggested that the 2 parasites may have had different diets. Host-specificity data for gnathiid isopods are scarce because the parasitic juvenile stages are difficult to identify and host-parasite contact is often brief. Engorged third stage gnathiids were photographed and permitted to moult into adults to allow identification. I compared mtDNA sequences from their blood meals to host sequences available on GenBank. The host frequency distributions used by each species were significantly different; only four host families were shared. I concluded that G. falcipenis and Gnathia sp C operate as preferential feeders. Importantly, this work showed that G. falcipenis was indeed a natural parasite of several species of damselfish (Pomacentridae) that could be collected as young recruits and used in manipulative experiments. I then used G. falcipenis as a model parasite to investigate the effects of isopods on recently recruited Dischistodus perspicillatus and small juvenile Acanthochromis polyacanthus damselfishes. Working with honours student Ms Rose Penfold, we determined that A. polyacanthus was infected by gnathiids in the wild at sizes as small as 4.2 mm SL. Laboratory infections revealed that larger A. polyacanthus were much better at eating gnathiids, a behaviour which prevented infection, and that smaller fish were more likely to die post-infection. Infection prevalence was > 3 % during the day, but we could not sample fish for nocturnal infection prevalence. A caging experiment suggested that most micropredation on damselfish took place at night. For D. perspicillatus, I found that exposure to 2 parasites each evening for 7 nights after settlement halved the growth of these fish. Lastly, numerous free-swimming cymothoid isopods were found associated with larval fish in light traps. Cymothoids have a multi-morphic life cycle composed of micropredatory stages that eventually become females, which are permanently attached to fishes. Because cymothoid taxonomy is based around female morphology, natatory-stage cymothoids can not be identified. I sequenced mtDNA from natatory and adult female life history stages and matched 4 of 11 natatory cymothoid morphotypes. Molecular data were also used to produce a phylogeny exploring the evolution of different forms of host attachment within the Cymothoidae. This phylogeny suggests that external attachment, formerly thought to be plesiomorphic, is a derived condition and has evolved several times independently. I suggest that attachment to the buccal cavity or gills is a primitive form of attachment. This research has provided information on emergence patterns and hostspecificity which is necessary for the future study of isopod vector biology. It also provides a platform for future taxonomic and phylogenetic studies on cymothoids. I demonstrate that gnathiids infect juvenile coral reef fish and suggest that they may influence survival both directly and indirectly by reducing growth and predisposing infected fish to size-selective mortality. Thus, interactions between isopod micropredators and recruiting fishes may determine the survivorship of individual fish and influence the subsequent community structure.

Identiferoai:union.ndltd.org:ADTP/252408
CreatorsJones, Conor McNamara
Source SetsAustraliasian Digital Theses Program
Detected LanguageEnglish

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