An outbreak of philophthalmosis in Larus michahellis and Larus fuscus gulls in Iberian Peninsula

Trematodes of the genus Philophthalmus Loos, 1899 are the eye parasites of birds and mammals, which use freshwater snails as their first intermediate hosts. Here we examined the presence of philophthalmids in a total of 1515 gulls (589 Larus fuscus and 926 Larus michahellis) admitted between January 2010 and October 2016 for rehabilitation at Olhão (Portugal), by the use of combined morphological and molecular analysis. We recorded the first infected L. fuscus and L. michahellis in July and November 2015, respectively. The philophthalmids were located in the conjunctival sac or under the nictitating membrane. Gulls infected with Philophthalmus lucipetus Rudolphi, 1819 presented no clinical signs, while those infected with Philophthalmus lacrymosus Braun, 1902 presented serious eye damage in the same host species. The prevalence of P. lucipetus reached 3.6% in L. fuscus and 0.8% in L. michahellis; the prevalence of P. lacrymosus reached 0.3% and 0.0%, respectively. The outbreak of P. lucipetus likely started in a narrowly defined area, since the first six cases, found between July and October 2015, originated from a single municipality, and only later more cases started to be retrieved from other municipalities of Portugal. These findings represent the first records of both philophthalmids in the Iberian Peninsula, their first records in L. michahellis and the first record of P. lacrymosus in L. fuscus. Further follow-up of the outbreak and the identification of intermediate hosts are needed.     

Lactate dehydrogenase in two digenetic trematodes and their host

Polyacrylamide gel electrophoresis of the two digenetic trematodes, Gigantocotyle explanalum from the liver and Gastrothylax crumenifer from the rumen of the water buffalo, Bubalus bubalis revealed the presence of at least six and seven isoenzymes of lactate dehydrogenase (LDH), respectively in a partially purified enzyme preparation. The respective host tissues showed five isoenzymes of LDH, which are characteristic to the vertebrates. Both parachloromercuribenzoate and iodoacetate affected the LDH activity of the parasites and host tissues differently. Spectrophotometric analysis also showed different specific activity and susceptibility to the action of thiol inhibitors. The host LDH was quite stable at 57°C for 30 min, but that of the parasites was less stable.     

Larval trematode antagonism: principles and possible application as a control method

The main features of trematode antagonism are reviewed briefly, and results of recent field experiments to test whether trematode antagonism can be used for control of trematode infections are discussed. These results show that it is easy to control trematode infections by dispersing large numbers of eggs of a dominant parasite in relatively small bodies of water. Such release may produce a multiple effect: (1) intertrematode antagonism; (2) considerable decrease in the snail population due to higher mortality and parasitic castration of infected snails; and (3) a microsporidan epidemic caused by a hyperparasite, affecting rediae and sporocysts and leading to suppression of cercarial production. Any one or a combination of the three effects may achieve control of the target species. The usefulness of this biological control method depends largely on whether dominant parasites can be found that fulfill the requirements for large-scale application and on whether other factors interfere with antagonism or prevent snails from becoming infected with the dominant speices. A good dominant trematode should be strongly antagonistic to the target species, have a wide geographic distribution, develop rapidly in the snail and cause complete castration, be easily maintained in the laboratory, and preferably be capable of infecting the snail hosts in their various habitats. Development of efficient methods of dispersing eggs and more field experiments are necessary to determine the advantages and limitations of this method.     

Cytological investigations on two species of allocreadiid trematodes with special reference to the occurrence of triploidy and parthenogenesis in Allocreadium fasciatusi

Karyotypes and cytological details of gametogenesis were analysed for Allocreadium handiai and A. fasciatusi. Mitotic plates studied in squashes of testes, ovary, eggs and intramolluscan stages showed that A. handiai is a diploid (2n = 14) with six pairs of submetacentrics and one pair of subtelocentrics. Total chromosome length of the diploid complement was 86.57 μm, the largest chromosome measured 8.87 μm (10.24% total chromosome length [TCL]) and the smallest was 2.83 μm (3.28% TCL). Squashes of testes revealed the presence of all stages of spermatogenesis with spermatocytes in various stages of meiotic activity and spermatids containing bundles of spermatozoa. Stages of development of the ovum conclusively proved that reproduction takes place by amphimixis. Mitotic figures of A. fasciatusi, on the other hand, revealed that it is a triploid (3n = 21) with three metacentrics, 12 submetacentrics and six subtelocentrics. The mean total chromosome length of the triploid complement was 137.54 μm. The largest chromosome measured 10.37 μm (7.54% TCL) and the smallest measured 2.67 μm (1.94% TCL). Spermatogenesis was abortive with no evidence of synaptic pairing and spermatozoa were not produced. Eggs remained unfertilized and reproduction was achieved by parthenogenesis which is of mitotic type. The karyotypes of the two species differed not only in the ploidy level but also in the centromeric indexes of certain chromosomes.     

Native Parasites Adopt Introduced Bivalves of the North Sea

Introduced species may have a competitive advantage over native species due to a lack of predators or pathogens. In the North Sea region, it has been assumed that no metazoan parasites are to be found in marine introduced species. In an attempt to test this assumption, we found native parasites in the introduced bivalves Crassostrea gigas and Ensis americanus with a prevalence of 35% and 80%, respectively, dominated by the trematode Renicola roscovita. When comparing these introduced species with native bivalves from the same localities, Mytilus edulis and Cerastoderma edule, trematode intensity was always lower in the introduced species. These findings have three major implications: (1) introduced bivalves are not free of detrimental parasites which raises the question whether introduced species have an advantage over native species after invasion, (2) introduced bivalves may divert parasite burdens providing a relief for native species and (3) they may affect parasite populations by influencing the fate of infectious stages, ending either in dead end hosts, not being consumed by potential final hosts or by adding new hosts. Future studies should consider these implications to arrive at a better understanding of the interplay between native parasites and introduced hosts.     

Life history, ecology and parasite community structure in Soviet birds

The paper describes an investigation of parasite richness in relation to host life history and ecology using data from an extensive survey of helminth parasites (cestodes, trematodes and nematodes) in Soviet birds. Correlates of parasite richness (number of parasite species per host species) were sought among 13 life-history variables, 13 ecological variables and one non-biological variable (number of host individuals examined) across a sample of 158 species of host. A statistical method to control for the effects of phylogenetic association was adopted throughout. Parasite richness correlates positively with the number of hosts examined (sample size) in all three parasite groups. Positive correlations (after controlling for the effects of sample size) were also found between host body weight and parasite richness for trematodes and nematodes, but not for cestodes.
A number of ecological variables were associated with parasite richness. However, when the effects of sample size and body weight were controlled for, only a single significant correlation (an association between trematode richness and aquatic habitat) remained. Similarly, a number of significant correlates of parasite richness were found among the life-history variables examined. Though several of these were robust to the confounding effects of sample size, all could be explained by the co-variation between life-history traits and body weight among the host species under investigation.     

Parasites and the avian spleen: helminths

A comparative analysis of the relationship between the spleen–a major organ of immunity and helminths was undertaken with bird species, using the phylogenetic regression technique. Species in which many individuals are infected with nematodes relative to the number of individuals examined for the presence of helminths (termed 'relative nematode presence') have significantly larger spleens, for a given body weight, in females (though not in males). There was little indication that this relationship depends on incidental ecological indices, the weights of other organs, or the 'relative presences' of trematodes, cestodes or haematozoa. Combined with previous, experimental, work it suggests that the avian spleen is important in resisting nematodes. Body weight is correlated with the relative presence of helminths; but even after removing body size effects, bird species which tend to be infected with trematodes are also more likely to be infected with cestodes. This paper indicates that the spleens of wild bird species are associated with macroparasites in the natural environment.     

Differential Parasitism of Native and Introduced Snails: Replacement of a Parasite Fauna

The role of parasites in a marine invasion was assessed by first examining regional patterns of trematode parasitism in the introduced Japanese mud snail, Batillaria cumingi (= B. attramentaria), in nearly all of its introduced range along the Pacific Coast of North America. Only one parasite species, which was itself a non-native species, Cercaria batillariae was recovered. Its prevalence ranged from 3 to 86%. Trematode diversity and prevalence in B. cumingi and a native sympatric mud snail, Cerithidea californica, were also compared in Bolinas Lagoon, California. Prevalence of larval trematodes infecting snails as first intermediate hosts was not significantly different (14% in B. cumingi vs 15% in C. californica). However, while the non-native snail was parasitized only by one introduced trematode species, the native snail was parasitized by 10 native trematode species. Furthermore, only the native, C. californica, was infected as a second intermediate host, by Acanthoparyphium spinulosum(78% prevalence). Given the high host specificity of trematodes for first intermediate hosts, in marshes where B. cumingi is competitively excluding C. californica, 10 or more native trematodes will also become locally extinct.     

Local diversity reduces infection risk across multiple freshwater host‐parasite associations

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Ecosystem consequences of fish parasites*

In most aquatic ecosystems, fishes are hosts to parasites and, sometimes, these parasites can affect fish biology. Some of the most dramatic cases occur when fishes are intermediate hosts for larval parasites. For example, fishes in southern California estuaries are host to many parasites. The most common of these parasites, Euhaplorchis californiensis, infects the brain of the killifish Fundulus parvipinnis and alters its behaviour, making the fish 10–30 times more susceptible to predation by the birds that serve as its definitive host. Parasites like E. californiensis are embedded in food webs because they require trophic transmission. In the Carpinteria Salt Marsh estuarine food web, parasites dominate the links and comprise substantial amount of biomass. Adding parasites to food webs alters important network statistics such as connectance and nestedness. Furthermore, some free‐living stages of parasites are food items for free‐living species. For instance, fishes feed on trematode cercariae. Being embedded in food webs makes parasites sensitive to changes in the environment. In particular, fishing and environmental disturbance, by reducing fish populations, may reduce parasite populations. Indirect evidence suggests a decrease in parasites in commercially fished species over the past three decades. In addition, environmental degradation can affect fish parasites. For these reasons, parasites in fishes may serve as indicators of environmental impacts.