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Parasites are usually considered to use their hosts as a resource for energy. However, there is increasing awareness that parasites can also become a resource themselves and serve as prey for other organisms. Here we describe various types of predation in which parasites act as prey for other organisms: (1) predation of nonhosts on infected hosts (concomitant predation), (2) predation on free-living parasite life cycle stages, (3) predation on ectoparasites in form of grooming or cleaning and (4) predation or hyperparasitism by other parasites. In many cases, these types of predation significantly reduce the numbers of parasites and thus affect parasite population dynamics. In contrast, predation on parasites is often beneficial for the hosts as they are released from parasite burden. Finally, when parasites act as prey they may contribute to the nonhost predator's diet, in some cases constituting a significant proportion of energy intake.
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Parasites as Prey
Anouk Goedknegt,
NIOZ Royal Netherlands Institute for Sea Research, Texel,
The Netherlands
Jennifer Welsh,
NIOZ Royal Netherlands Institute for Sea Research, Texel, The Netherlands
David W Thieltges,
NIOZ Royal Netherlands Institute for Sea Research, Texel,
The Netherlands
Parasites are usually considered to use their hosts as a
resource for energy. However, there is increasing aware-
ness that parasites can also become a resource themselves
and serve as prey for other organisms. Here we describe
various types of predation in which parasites act as prey
for other organisms: (1) predation of nonhosts on
infected hosts (concomitant predation), (2) predation on
free-living parasite life cycle stages, (3) predation on
ectoparasites in form of grooming or cleaning and (4)
predation or hyperparasitism by other parasites. In many
cases, these types of predation significantly reduce the
numbers of parasites and thus affect parasite population
dynamics. In contrast, predation on parasites is often
beneficial for the hosts as they are released from parasite
burden. Finally, when parasites act as prey they may con-
tribute to the nonhost predator’s diet, in some cases
constituting a significant proportion of energy intake.
In ecological studies, parasites are usually not considered
to serve as prey or a resource for other organisms. Instead,
by definition, they use other organisms as a resource
themselves. However, recent studies on food webs includ-
ing parasites have shown that parasites are involved in 75%
of the trophic links between species in a food web, including
many links where they are a resource for other organisms
(Lafferty et al., 2006a). There are several different ways in
which parasites can be involved in trophic links in food
webs. First of all, many parasites depend on the predation
of their hosts for successful transmission to the succeeding
down-stream host during some part of their complex life
cycles, thus hitch-hiking on predation links (a transmission
type called trophic transmission). However, not all preda-
tors of infected organisms are suitable down-stream hosts
and parasites may thus be ‘accidentally’ and indirectly
consumed by predators and, therefore, not result in suc-
cessful transmission. Parasites may also directly become
prey during their free-living life cycle stages. Most parasites
include free-living stages to get from one host to the next. In
this free-living stage, parasites are extremely vulnerable to
predation by nonhost predators. Another type of direct
predation on parasites involves parasites that attach
themselves to the outside of their hosts (ectoparasites).
Ectoparasites may also be vulnerable and can be consumed
by other animals. Finally, parasites can also serve as prey or
host resources for other parasites. In the following, we
explain the different cases where parasites become prey and
discuss the ecological effects of predation on parasites for
the parasites, their hosts and the predators. See also:Food
Webs;Parasites and Pathogens: Avoidance;Parasitism:
Life Cycles and Host Defences against Parasites;Parasit-
ism: the Variety of Parasites;Parasitoids
Predation and Transmission
Trophic transmission
By definition, parasites are always dependant on the pres-
ence of their hosts. However, all parasites have to transmit
from one host to another at some point in their lives. They
do so by an infective life cycle stage, whereby the parasite is
one free living and released into the environment. If the
parasite has a direct life cycle, the infective stage can infect
conspecific hosts or, in the case of parasites with complex
life cycles, other hosts. The latter types of parasites often
include more than one free-living stage in their life cycle by
which the parasites go through a specific sequence of
parasitic stages in hosts and free-living stages. This is
illustrated by the typical three-host life cycle of digenan
trematodes, a type of parasitic flat worm which are often
referred to as ‘flukes’ (
Figure 1
). In these trematodes,
Advanced article
Article Contents
Predation and Transmission
Concomitant Predation
Predation on Free-Living Stages
Predation on Ectoparasites
Parasites as Consumers of Parasites
Online posting date: 17
September 2012
eLS subject area: Ecology
How to cite:
Goedknegt, Anouk; Welsh, Jennifer; and Thieltges, David W
(September 2012) Parasites as Prey. In: eLS. John Wiley & Sons, Ltd:
DOI: 10.1002/9780470015902.a0023604
eLS &2012, John Wiley & Sons, Ltd.
infection of the next hosts in the life cycle (down-stream
hosts) not only occurs via free-living infective stages but
also via predation of infected hosts (
Figure 1
). The second
intermediate host (up-stream host; a bivalve in
Figure 1
needs to be consumed by the definitive host (the down-
stream host; a bird in
Figure 1
) before the parasite can
develop into its adult stage and sexually reproduce. In this
life cycle stage, predation of its up-stream host is the only
way for the parasite to successfully complete its life cycle.
Almost all parasites with complex life cycles follow
predator–prey links and depend on trophic transmission at
some point in their lives; thus predation and transmission
are intricately linked for many parasites (Lafferty et al.,
2008). The importance of trophic transmission for
parasites is illustrated in a food web from a saltmarsh in
California, where a third of the parasite species consumed
by predators via their prey use the predator as host
(Lafferty et al., 2006b).
Parasites manipulate hosts to increase
As predation by down-stream hosts is often crucial for the
successful transmission of parasites, many parasite species
have developed strategies to increase their chances to
become transmitted via manipulating the behaviour of
their hosts. For example, one trematode species encysts
itself in the brain of killifish, an important prey item for
birds in the estuaries of California. When a killifish
becomes infected, it exhibits behaviours that make it more
conspicuous (e.g. surfacing or flashing), making the fish
10–30 times more vulnerable for predation by birds, the
definitive host of the parasite (Lafferty and Morris, 1996).
Another example is that of the so-called ‘zombie snails’.
These snails are infected by a trematode that uses birds as
definitive host (Lewis, 1977). When a snail is infected by a
parasite egg, the egg develops into a sporocyst, which
contain hundreds of little parasitic clones (also called
‘brood-sacs’), which subsequently invade the snail’s ten-
tacles. As the tentacles become more swollen and colourful
they start to mimic the appearance of a caterpillar (
Figure 2
This alteration to the host caused by the parasite lures birds
to eat the tentacles of the snail host and can result in the
parasite infecting the bird. The parasite also has another
tactic to increase the likelihood of predation by the bird.
The infection of the parasite in the tentacles reduces the
ability of the snail to react to light intensity. As a result, the
snail may no longer hide in the shadow as it would do
normally and, therefore, it is more visible for predators.
Furthermore, the brood-sacs in the tentacles start to pul-
sate in response to light intensity (Wesenberg-Lund, 1934),
making the resemblance to a caterpillar even more likely.
These examples illustrate that parasites can mediate overall
predation rates and predator–prey choice, depending on
the infection levels in a host population. By doing so, they
can also affect the flow of energy through a food web.
Concomitant Predation
Trophic transmission gone wrong
Predation of infected hosts does not always lead to a suc-
cessful transmission. In most cases, the predator will
actually be an unsuitable host for the parasite. In this case,
Figure 1 Example of a typical three-host life cycle of a trematode,
showing the sequence of different hosts and free-living stages involved
(black arrows) and illustrating the different types of predation on them
(blue arrows). In this case, the definitive host is a bird, from which the
parasites release free-living eggs into the water together with the bird’s
faeces. The eggs infect a first intermediate host (a gastropod), in which the
parasite reproduces asexually in so-called sporocysts or rediae and releases
a second free-living stage into the water (cercariae). These cercariae infect a
second intermediate host (a cockle) in which the parasites encyst
(metacercariae). Finally, when the second intermediate host is consumed
by the definitive host, the life cycle of the parasite is completed. Parasites
can become prey either when infected hosts are consumed by nonhosts
(concomitant predation; filled blue arrows) or when their free-living stages
are consumed (open blue arrows). Note that parasite consumption is also
an essential part of the parasite’s life cycle when the infected second
intermediate host is eaten by the definitive host.
Parasites as Prey
eLS &2012, John Wiley & Sons, Ltd.
the potential (but unsuitable) host acts as a predator,
leading to consumption rather than transmission of the
parasite (Johnson et al., 2010). In the example of the tre-
matode life cycles (
Figure 1
), first or second intermediate
hosts as well as the definitive hosts may be preyed on by
nonhost predators, consuming the parasites together with
their prey without becoming infected. This type of acci-
dental predation has been termed concomitant predation
(Johnson et al., 2010; filled blue arrows in
Figure 1
). For
trophically transmitted parasites, this seems like an
unavoidable side effect of being dependent on predation
links for transmission: whilst predation will sometimes
ensure transmission, it will probably more often lead to
ending up in the wrong host. Interestingly, concomitant
predation does not need to lead to the total consumption of
the host. For example, one trematode species prevents New
Zealand cockles (Austrovenus stutchburyi) from burying in
the sediment by encysting itself in the cockle’s foot and
interfering with the musculature. As a result, the cockles lay
on the sediment surface where they are more vulnerable to
predation by birds than their uninfected conspecifics bur-
ied in the sediment (Mouritsen and Poulin, 2003). This is
usually interpreted as a case of parasite manipulation as the
parasite’s down-stream hosts are birds. However, infected
cockles on the sediment surface are often not completely
eaten by birds (suitable hosts), but partially consumed by
benthic fishes (unsuitable hosts). The fishes feed on the
highly infected tip of the cockles’ feet, a behaviour that is
referred to as foot cropping. In manipulative experiments,
the scientists found that this partial foot cropping by
fish occurs to such an extent that it exceeds total predation
by birds. As a result, only 2.5% of the parasites are
actually transferred to their down-stream hosts, whereas
17.1% are lost to the fish (Mouritsen and Poulin, 2003;
Figure 3
Increased parasite mortality and changes in
prey quality
The cockle example illustrates how concomitant predation
can significantly contribute to parasite mortality. Food
web studies that include parasites suggest that approxi-
mately 63% of the links where a predator consumes
infected hosts lead to concomitant predation because the
predator is an unsuitable host, but only approximately
37% of these links result in the transmission of parasites
(Lafferty et al., 2006b). However, to date, little is known on
the actual magnitude of the effect of concomitant predation
on parasite population dynamics.
For a predator, concomitant predation may result in
an additional food resource, specifically when the host is
highly infected. However, again, to date, there are no
studies regarding the potential energy gain that predators
get from consuming parasites alongside their actual prey.
In contrast, more is known on the effects of parasites on
the general energetic value of their hosts. Infected prey
may have a reduced or increased quality for predators,
depending on the parasite–host system. For example,
brine shrimps which are infected by tapeworm larvae
have a higher energy content (including the parasite)
compared to uninfected conspecifics (Sa
´nchez et al.,
2009). In contrast, fungal infections of Daphnia reduce
the energetic value of infected hosts (again including the
parasites) for their juvenile fish predators (Forshay et al.,
Besides directly affecting the energetic value of their
hosts, parasites may also have indirect effects on pre-
dation rates of predators. Similar to the host manipula-
tion in trophically transmitted parasites discussed above,
parasites may influence predator–prey interactions in
nonhost predators. They can do so by making their hosts
more vulnerable to predation. For example, Daphnia
water fleas are more likely to be predated on by fish
predators when they are infected by a fungi, but the fish
do not serve as down-stream hosts (Johnson et al., 2006).
As a consequence of the infection, the body cavity of
Daphnia is filled with thousands of dark sporangia,
reducing its transparency and making it more visible
for fish predators. Another example of how parasites
can influence predator–prey interactions is the case of
the shell-boring polychaete Polydora ciliata. This worm
weakens the shell of the marine periwinkle Littorina
littorea, making infected snails more vulnerable to
predators. Interestingly, shore crabs make use of this
weakness, preferring infected snails over uninfected snails
(Bushbaum et al., 2007).
Figure 2 A ‘zombie snail’. The snail is infected by a trematode that
invades the snail’s tentacles, leading to swollen and colourful tentacles. This
mimics the appearance of a caterpillar, which is the prey of the parasite’s
definitive bird hosts. Hence, the phenotypic changes caused by the parasite
increase its transmission. Reproduced by permission of Marek Snowarski
Parasites as Prey
eLS &2012, John Wiley & Sons, Ltd.
Predation on Free-Living Stages
Vulnerable life cycle stage
As discussed above, many parasites have life cycle stages
which occur in a host and other stages whereby the parasite
is living freely in the environment (
). Once outside the
protection of a host, these free-living stages are vulnerable
to various abiotic and biotic factors (Thieltges et al., 2008b;
for abiotic examples see: Pietrock and Marcogliese, 2003).
For example, surrounding organisms can prey upon the
free-living stages, thereby reducing them in numbers. Some
predators prey selectively on these free-living stages such as
juvenile crab and shrimp, whereas others predate in a
nonselective way such as filter feeders. As a result, the
infection levels in the down-stream hosts decrease. This
process is called the ‘dilution effect’ and has been reported
for many different parasite–host systems (Thieltges et al.,
2008a; Johnson and Thieltges, 2010). Instead of direct
predation, free-living parasites can also be ingested toge-
ther with a totally different food source. For instance, dung
beetles and earth worms frequently ingest eggs and larvae
of parasitic nematodes when feeding on faeces of other
organisms (English, 1979; Waghorn et al., 2002).
Effects on parasites and application in pest
Many studies suggest that the various forms of predation
on free-living stages are important mortality factors for
parasites. Predators can, therefore, be very effective in
reducing numbers of free-living stages of parasites. For
example, copepods can reduce the number of juvenile
stages of mermithid nematodes by 70– 100%, depending on
the species of copepod and their density (Achinelly et al.,
2003). There are many other organisms that have been
reported to significantly reduce infective stages of nema-
todes, either directly or indirectly via ingestion with other
food (see
Figure 4
for examples). Similarly, many bivalves
like oysters and mussels have been shown to be effective
diluters, reducing the number of free-living stages of tre-
matodes by almost 80% (Thieltges et al., 2008b).
Such strong reductions in the numbers of infective parasite
stages have important implications for pest control in agri-
culture and livestock farming. One example is the reduction
of eggs of parasitic nematodes by a nematophagous fungi in
the intestines of swines (Ferreira et al., 2011). Normally, the
nematodes cause liver damage to the swine (‘milk spots’
caused by larvae), but the addition of a special fungi to the
swines’ feed reduced the numbers of eggs by more than 50%.
This is because the fungi excreted with the faeces reduce the
numbers of infective eggs on the pasture (
Figure 4
As free-living stages are usually produced in high num-
bers, they may also constitute an energy resource for
predators preying on them. For example, the production of
trematode cercariae in coastal marine systems exceeds the
standing stock of birds (Kuris et al., 2008). Many organ-
isms are known to prey on cercariae, suggesting that cer-
cariae may be a significant energy source for some
predators (Thieltges et al., 2008a). However, actual data of
Infected cockles
% of infected stages eaten
Uninfected cockles
Figure 3 Partial predation on infected hosts by a nonhost predator. A trematode species infecting the New Zealand cockle impairs its burying ability so that
cockles are exposed on the sediment, resulting in an increased predation by the definitive host compared to uninfected cospecifics (a case of host
manipulation). However, fish also partially prey on exposed infected cockles by nipping off the tip of the cockles’ foot. Most parasites are concentrated in the
foot tip and, since the fishes do not serve as down-stream hosts, a significant proportion of the parasites are lost via this concomitant predation.
Parasites as Prey
eLS &2012, John Wiley & Sons, Ltd.
the relevance of cercariae in the diet of nonhosts are
restricted to juvenile fish in a California estuary where
predation of cercariae was calculated to comprise
approximately 2–3% of the fishes’ energetic requirements
(Kaplan et al., 2009).
Predation on Ectoparasites
Grooming and cleaning
Another case where parasites become prey is predation on
ectoparasites, which are parasites that attach themselves to
the outside of the body of a host. A classic example of
predation on ectoparasites is grooming by monkeys. In this
type of intraspecific interaction, one individual releases a
second individual from fleas and other ectoparasites. This
is beneficial for the monkey that is groomed, but it also
strengthens the social bounding between both individuals.
Similar examples are known from interspecific inter-
actions, for example, from oxpeckers which free mammals
on the African savannahs of ticks (Hart et al., 1990) and
from cleaner shrimps and fishes which pick ectoparasites
from fish hosts (Grutter, 1999).
Effects on parasites, hosts and predators
For parasites, grooming and cleaning are probably often
significant sources of mortality, with negative effects on
parasite population dynamics. In contrast, grooming and
cleaning are beneficial for both, the host and the predator:
one species profits from the energy resource and the other
species is released from its parasite pressure. Hence, this
type of interaction can be considered to be mutualistic. The
benefit for hosts can be illustrated in the case of cleaner fish
that that feed on ectoparasites attached to the body of their
clients. When these cleaner fish are absent over a longer
period the hosts are negatively influenced by the ecto-
parasites. In a study over a 8.5-year period, Waldie et al.
(2011) found significantly smaller hosts in an area where no
cleaner fish were present, suggesting that these hosts had to
invest their energy in their immune system rather than
into growth. In addition, in the absence of cleaner fish, a
reduction of 65% in visiting juvenile hosts was observed.
The juveniles suffer from the absence of cleaner fish, as the
ectoparasites have a negative influence in their perform-
ance as measured by swimming and oxygen consumption
(Grutter et al., 2011). The cleaning symbiosis is also very
beneficial for the cleaners as ectoparasites may constitute a
large part of their diet (Grutter, 1996).
Ectoparasites can be a significant problem in aquaculture,
where high stocking densities often provide ideal habitats
for the parasites. A prominent example is ectoparasitic
salmon lice (a copepod), which feed on the fish tissue and
can cause morbidity and mortality (Pike and Wadsworth,
Figure 5a
). When a population of lice settles in the
cages where the salmon are raised (
Figure 5b
), the parasites
can spread easily due to a free-living life stage and the high
densities in which the fish are kept, resulting in declines of
salmon stocks in the cages (Connors et al., 2010). Even
more worrying is the fact that the free-living stages of the
parasite can also spill-over and infect wild populations of
salmon, as the salmon farms are often built in the proximity
of their migration routes (Costello, 2009). This spill-over
can cause up over 80% mortality in many runs of wild pink
salmon, when passing salmon farms on their way to the
open ocean (Krkos
ˇek et al., 2007). Since salmon lice are
such a problem, various treatments have been tested;
however these compounds often have undesired effects on
the fish or the environment (Roth et al., 1993). As an
alternative, it has been suggested to add cleaner fish or
shrimp into the net pens to reduce ectoparasite burden of
the fish (
Figure 5c
). For example, goldsinny wrasse (Cteno-
labrus rupestris) added to salmon cages can effectively
control sea lice (1– 8 sea lice per fish compared to up to 40 in
control cages; Treasurer, 1994). Similar results were
obtained with two species of cleaner fish on two Irish sal-
mon farms (Deady et al., 1995). By using a ratio of one
cleaner fish to 250 salmon, the lice levels were kept below
five lice per fish. In addition, the salmon were less stressed
by this type of pest control than conventional chemical
treatments. Furthermore, there are two species of cleaner
shrimps that inhabit North-Atlantic shallow waters and
remove ectoparasites from plaice (O
¨stlund-Nilssen et al.,
2005). These results suggest that cleaner shrimps and
cleaner fish could be suitable as biological control agents
for sea lice infections on salmon and other fish in aqua-
culture settings.
% Reduction of free-living stages
Dung beetles
Figure 4 Examples of the levels of reduction of infective free-living stages
of parasitic nematodes by various organisms from different ecosystems
(indicated by different colours): earth worms (Waghorn et al., 2002) and
dung beetles (English, 1979) preying on nematode eggs and larvae in
dung, copepods preying on nematode larvae in fresh water systems
(Achinelly et al., 2003), mites preying on nematode larvae in sandy soils
(Karagoz et al., 2007) and nematophagous fungi on nematode larvae on
livestock pasture (Ferreira et al., 2011).
Parasites as Prey
eLS &2012, John Wiley & Sons, Ltd.
Parasites as Consumers of Parasites
Hyperparasitism and intraguild predation
Finally, parasites can serve as a resource for other para-
sites, either by being parasitized by other parasites
(hyperparasitism) or by being preyed by other parasites
(intraguild predation). The first happens when a parasite
infects another parasite. This is particularly well demon-
strated within the insect order of Hymenoptera. These so-
called hyperparasitoids often infect a primary parasitoid,
which in turn infects a herbivorous or scavenger host
(Sullivan and Vo
¨lkl, 1999). The second happens when
parasites kill and consume other parasites, often in order to
get rid of potential competitors. For example, trematodes
infecting snails as first intermediate host can be preyed on
by other species of trematodes. Some of these predating
species develop a special cast of small ‘soldier morphs’ with
large mouths for this purpose. These ‘warrior worms’
attack other parasites trying to invade the snail host.
Another morph of large worms acts as reproductive cast
worms (Hechinger et al., 2011). Both morphotypes are
genetically identical as they are clones derived from a single
egg infecting the host snail. Hence, this shows an analogy to
the social organisation in colonies of ants or bees.
Hyperparasitism and pest control
The significant effect of hyperparasites on their hosts is
illustrated by the effective use of insect hyperparasitoids as
biological control agents against pest insects in agriculture.
Here, they can be very efficient in controlling pest popu-
lations. However, there are also cases where hyperparasites
Figure 5 Typical ectoparasites of salmon in aquaculture and their consumption by cleaner fishes: (a) salmon lice (parasitic copepods, the brown
ectoparasites) infect salmon and cause damage to the skin, often leading to secondary infections. Reproduced by permission of Bruce MacGregor Sandison.
(b) Salmon farm, where the high stocking densities are ideal habitats for the transmission of the copepods (with a direct life cycle) from one host to another.
Reproduced by permission of The Atlantic Salmon Trust. (c) A cod with a cleaner fish, preying on ectoparasites like copepods. Reproduced by permissionof
Alexandra Grutter.
Plant host
Introduced parasitoid:
Control agent
Target pest
Native hyperparasitoids
Figure 6 Example of a parasitoid, introduced to control a plant pest,
which then became host to native parasitoids, thus becoming
hyperparasitoids. The cassava plant is defoliated by the South American
mealybug, an unwanted herbivore. As a control for this pest, a parasitoid
from the order Hymenoptera was introduced. This parasitoid, in turn, was
exploited by 10 native species of parasitoids.
Parasites as Prey
eLS &2012, John Wiley & Sons, Ltd.
can infect the ‘good’ parasite that was initially introduced
for pest control. For example, a nonindigenous wasp of the
order Hymenoptera is used to protect cassave plants from
the South American mealybug in Africa (Herren and
Neuenschwander, 1991;
Figure 6
). The original infection
success of the wasp was so high that even the defence
mechanisms of the mealybug did not stop the biological
control (Sullivan and Neuenschwander, 1988). However,
the new wasp was soon itself used as a host by at least 10
native species of hyperparasitoids. The native wasps infect
the introduced control agent in occasional but very high
levels despite, on average, having no detrimental effect on
the control efficiency (Neuenschwander, 1996).
The examples above demonstrate that there are numerous
ways of how parasites can act as prey for other organisms.
In many cases, predation on parasites can have important
consequences for parasite population dynamics, the
infection burden of their hosts and possibly also for the
energy intake of nonhosts. The few studies that integrated
predation on parasites as trophic links in food web studies
indicate that such predation is very common. Studying the
strength of these links in future studies will increase our
understanding of disease dynamics as well as the topology
and functioning of food webs.
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Further reading
Johnson PTJ, Dobson A, Lafferty KD et al. (2010) When parasites
become prey: ecological and epidemiological significance of
eating parasites. Trends in Ecology and Evolution 25: 362– 371.
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factors in the transmission of free-living endohelminth stages.
Parasitology 135: 407–426.
Parasites as Prey
eLS &2012, John Wiley & Sons, Ltd.
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Phenotypic polymorphism is a commonly observed phenomenon in nature, but extremely rare in free-living stages of parasites. We describe a unique case of somatic polymorphism in conspecific cercariae of the bird schistosome Trichobilharzia sp. “peregra”, in which two morphs, conspicuously different in their size, were released from a single Radix balthica snail. A detailed morphometric analysis that included multiple morphological parameters taken from 105 live and formalin-fixed cercariae isolated from several naturally infected snails provided reliable evidence for a division of all cercariae into two size groups that contained either large or small individuals. Large morph (total body length of 1368 and 1339 μm for live and formalin-fixed samples, respectively) differed significantly nearly in all morphological characteristics compared to small cercariae (total body length of 976 and 898 μm for live and formalin samples, respectively), regardless of the fixation method. Furthermore, we observed that small individuals represent the normal/commonly occurring phenotype in snail populations. The probable causes and consequences of generating an alternative, much larger phenotype in the parasite infrapopulation are discussed in the context of transmission ecology as possible benefits and disadvantages facilitating or preventing the successful completion of the life cycle.
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Sloths are unusual mobile ecosystems, containing a high diversity of epibionts living and growing in their fur as they climb slowly through the canopies of tropical forests. These epibionts include poorly studied algae, arthropods, fungi, and bacteria, making sloths likely reservoirs of unexplored biodiversity. This review aims to identify gaps and eliminate misconceptions in our knowledge of sloths and their epibionts, and to identify key questions to stimulate future research into the functions and roles of sloths within a broader ecological and evolutionary context. This review also seeks to position the sloth fur ecosystem as a model for addressing fundamental questions in metacommunity and movement ecology. The conceptual and evidence-based foundation of this review aims to serve as a guide for future hypothesis-driven research into sloths, their microbiota, sloth health and conservation, and the coevolution of symbioses in general.
METODOLOGI PENELITIAN DI BIDANG PARASITOLOGI KEDOKTERAN Parasitologi Kedokteran adalah cabang ilmu Kedokteran yang terus berkembang. Eksplorasi terhadap agen-agen parasitik serta faktor-faktor yang mempengaruhinya salah satunya dilakukan melalui penelitian. Penelitian yang baik, apapun bidangnya, seharusnya mampu menjawab pertanyaan penelitiannya serta menyisakan ruang buat orang lain untuk mengeksplorasi topik yang diteliti secara lebih mendalam. Dengan demikian dapat dikatakan tujuan paling mulia dari sebuah penelitian adalah untuk membuat hidup menjadi lebih baik. Untuk melakukan hal tersebut maka diperlukan metodologi penelitian yang benar. Buku sederhana ini dituliskan buat mahasiswa Fakultas Kedokteran atau rumpun ilmu Kesehatan lain yang berminat untuk melakukan penelitian di bidang Parasitologi Kedokteran. Isinya mencakup tahapan ilmiah, metodologi penelitian serta disain penelitian yang lazim digunakan di bidang Parasitologi. Penulisan buku ini tidak dimaksudkan untuk menggantikan buku-buku yang sudah ada, melainkan menjembatani ‘celah’ diantara bidang Metodologi Penelitian dengan bidang Parasitologi Kedokteran. Penulis berharap karya ini dapat menjadi salah satu sumber referensi bagi peneliti atau pembelajar untuk memperdalam dan bahkan mempraktekkan pengetahuan dalam bidang Metodologi Penelitian di bidang Parasitologi Kedokteran.
1. Parasites are one of the main actors in host–parasite interactions. Still, their role as a prey and the related consequences for such interactions and in other respects, such as food webs, are frequently overlooked. 2. This paper analyses predation pressure on a ubiquitous avian ectoparasitic fly, Carnus hemapterus, identifies their main natural enemies and quantifies their relative effect on the abundance of the parasite. Also, the effect of nest‐site type on their main enemies' predation pressure was analysed. 3. Several ant species were found in the nest boxes of the host species, the European roller (Coracias garrulus), during the breeding season and preyed upon adult and larval stages of Carnus. 4. Ants were also the putative predators of carnid pupae after the breeding season, when significant reduction (on average, by half) in the abundance of carnid pupae occurred in 75% of nest boxes within few months. 5. Carnid pupae are also reported here, for the first time, to be parasitised by the parasitoid wasp Chartocerus conjugalis, whose prevalence was around 21%. 6. Nest‐site type had no clear effect on the predation rate of carnid pupae after the breeding season. 7. It was concluded that predation is an important factor regulating the abundance of ectoparasites, and thus, it may influence the outcome of host–parasite relationships.
Free‐living parasite life stages may contribute substantially to ecosystem biomass and thus represent a significant source of energy flow when consumed by non‐host organisms. However, ambient temperature and the predator’s own infection status may modulate consumption rates towards parasite prey. We investigated the combined effects of temperature and predator infection status on the consumer functional response of three‐spined sticklebacks towards the free‐living cercariae stages of two common freshwater trematode parasites (Plagiorchis spp., Trichobilharzia franki). Our results revealed genera‐specific functional responses and consumption rates towards each parasite prey: Type II for Plagiorchis spp. and Type III for T. franki, with an overall higher consumption rate on T. franki. Elevated temperature (13 ºC) increased the consumption rate on Plagiorchis spp. prey for sticklebacks with mild cestode infections (<5% fish body weight) only. High consumption of cercarial prey by sticklebacks may impact parasite population dynamics by severely reducing or even functionally eliminating free‐living parasite life stages from the environment. This supports the potential role of fish as biocontrol agents for cercariae with similar dispersion strategies, in instances where functional response relationships have been established. Our study demonstrates how parasite consumption by non‐host organisms may be shaped by traits inherent to parasite transmission and dispersal, and emphasizes the need to consider free‐living parasite life stages as integral energy resources in aquatic food webs.
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Parasitic dinoflagellates of the genus Amoebophrya infect free-living dinoflagellates, some of which can cause harmful algal blooms (HABs). High prevalence of Amoebophrya spp. has been linked to the decline of some HABs in marine systems. The objective of this study was to evaluate the impact of Amoebophrya spp. on the dynamics of dinoflagellate blooms in Salt Pond (MA, USA), particularly the harmful species Alexandrium fundyense. The abundance of Amoebophrya life stages was estimated 3-7 days per week through the full duration of an annual A. fundyense bloom using fluorescence in situ hybridization coupled with tyramide signal amplification (FISH- TSA). More than 20 potential hosts were recorded including Dinophysis spp., Protoperidinium spp. and Gonyaulax spp., but the only dinoflagellate cells infected by Amoebophrya spp. during the sampling period were A. fundyense. Maximum A. fundyense concentration co-occurred with an increase of infected hosts, followed by a massive release of Amoebophrya dinospores in the water column. On average, Amoebophrya spp. infected and killed ∼30% of the A. fundyense population per day in the end phase of the bloom. The decline of the host A. fundyense population coincided with a dramatic life-cycle transition from vegetative division to sexual fusion. This transition occurred after maximum infected host concentrations and before peak infection percentages were observed, suggesting that most A. fundyense escaped parasite infection through sexual fusion. The results of this work highlight the importance of high frequency sampling of both parasite and host populations to accurately assess the impact of parasites on natural plankton assemblages.
Full-text available
Salt marshes provide a model ecosystem for analyzing the role of parasites in community dynamics. These habitats include an abundant and diverse community of trematode parasites which have complex life cycles, including snail, fish and bird hosts, embedded in rich food webs. Parasites were added to an already detailed food web from the Carpenteria salt marsh in Santa Barbara, California. Including parasites in the food web dramatically increased food web connectance (the average level of species interaction), which has profound implications for the study of community structure and function. Further incorporation of parasites into food webs will increase our appreciation of their role in ecosystems.
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Crab predation may profoundly affect the structure of marine benthic mollusc populations and prey choice of crabs may be altered by organisms associated with their prey. We investigated effects of the shell-boring polychaete Polydora ciliata on shell strength of the periwinkle Littorina littorea, and the concomitant prey selectivity of one of its major predators, the crab Carcinus maenas. Shell strength of periwinkles measured as force required to cause cracking was significantly lower in snails infected with P. ciliata than those without infection. In laboratory predation experiments, C. maenas consumed more snails infected with P. ciliata than uninfected periwinkles in a given size class. This was true when infected and uninfected snails were offered independently and simultaneously. Although C. maenas preferred small-sized (13 to 17 mm shell height) over medium (18 to 21 mm) and large (22 to 24 mm) periwinkles, consumption of large snails with P. ciliata was twice as high as for medium-sized L. littorea without polychaetes. Thus, this shell-boring polychaete causes crabs to shift their prey choice, and may even eliminate a size refuge for large infected periwinkles. We conclude that P. ciliata modifies predator-prey interactions, and we propose more generally that a high prevalence of shell-colonising organisms may exert a strong indirect effect on the dynamics and size distributions of mollusc populations.
Full-text available
Parasites that are transmitted from prey to predator are often associated with altered prey behavior. Although many concur that behavior modification is a parasite strategy that facilitates transmission by making parasitized prey easier for predators to capture, there is little evidence from field experiments. We observed that conspicuous behaviors exhibited by killifish (Fundulus parvipinnis) were associated with parasitism by larval trematodes. A field experiment indicated that parasitized fish were substantially more susceptible to predation by final host birds. These results support the behavior-modification hypothesis and emphasize the importance of parasites for predator-prey interactions.
The rate at which parasites (mainly gnathiid isopod larvae) were removed from fish by the cleaner wrasse Labroides dimidiatus was investigated. To examine the effect of this parasite removal on the parasites of fish, the number of parasites removed per individual host fish Hemigymnus melapterus per day was estimated and compared to the infection rate and abundance of gnathiids on H. melapterus. The study was conducted at Lizard Island, Great Barrier Reef, Australia, using a combination of observations of the feeding rates of cleaners, estimates of how much time individual hosts spend being cleaned, cleaner fish stomach content analyses, and a gnathiid manipulation experiment. The frequency and duration of inspection by L. dimidiatus were measured to provide an estimate of the feeding rate. Individual L. dimidiatus spent on average 256 ± 11 (SE) min d-1 inspecting 2297 ± 83 fish. L. dimidiatus consumed a large number of parasites (1218 ± 118, mainly gnathiid isopods) each day. The estimated predation rate by L. dimidiatus was 4.8 ± 0.4 parasites per minute of inspection or).5 ± 0.05 parasites per inspection. The infection rate of gnathiids onto fish was high, with reduced gnathiid loads (by about 50%) of fish returning to levels similar to control fish within 1 to 6 d. These high infection rates suggest that a significant proportion of gnathiids removed by cleaner fish are quickly replaced. The high predation rate relative to the number of gnathiids on fish and their infection rate shows that cleaner fish have an effect on the abundance of gnathiids on fish.
The cleaning of client fish by cleaner fish is one of the most highly developed interspecific communication systems known. But even though it is a seemingly obvious mutualism1, 2, several quantitative studies3, 5 have failed to show any benefit for the clients, leading to the hypothesis that cleaner fish are 'behavioural parasites' that exploit the sensory system of the clients6 to obtain food, rather than to increase the client's fitness. The cleaner fish Labroides dimidiatus eats parasitic gnathiid isopods, which decline in number on the client fish Hemigymnus melapterus daily between dawn and sunset7, 8. I find that the cleaner fish reduces parasite abundance, resulting in a 4.5-fold difference within 12 hours, supporting the hypothesis that cleaning behaviour is mutualistic.
The encyrtid wasp Epidinocarsis lopezi (De Santis) has been introduced into Africa as a biological control agent against the cassava mealybug Phenacoccus manihoti Matile-Ferrero. This host has a defense reaction against the immature parasitoid that involves encapsulation and melanization. Under laboratory conditions, 37.5% of once-stung cassava mealybugs had been parasitized, as indicated by eggs and larvae of the parasitoid in dissected hosts. Of these parasitized cassava mealybugs, 89.6% contained melanized particles (egg, partially melanized larva, internal host tissues, exoskeleton wound scars). Some of the parasitoid larvae were only partially melanized, and either freed themselves from the melanized capsule or else shed it at the next molt. By the 3rd day of their development only 12.5% were completely melanized. In cassava mealybugs with melanized host tissue but no living parasitoid, the survival of the host was not affected by the melanization. The mealybug itself sometimes shed black particles at the next molt and these were found attached to the cast skins. When superparasitized in the laboratory, 68.6% of twice-stung cassava mealybugs contained parasitoids. Mummies collected from a field experiment showed that melanization rates of mummies increased with increasing parasitization rates. Thus, melanization in the cassava mealybug was commonly triggered when E. lopezi oviposited, but this defense reaction was mostly ineffective, permitting the introduced parasitoid to be a successful biological control agent in Africa against the cassava mealybug, a major pest on this important food crop.
Feeding electivity and daily food consumption by a cleaner fish goldsinny wrasse, Ctenolabrus rupestris (L.) on sea lice, Lepeophtheirus salmonis Krøyer, on farmed Alantic salmon, Salmo salar L., was assessed by comparison of lice numbers and developmental stages on salmon in pens with and without wrasse. Mobile stages of L. salmonis in the pen with wrasse remained low (1–8 per fish) with no requirement for chemical treatment compared with a heavy infestation (up to 50) on the control pen. Wrasse selectively preyed on the larger lice stages, mainly adults and female pre-adult Stage II, and this was measured and statistically tested using Pearre's selection index. The mean number of mobile L. salmonis consumed daily by an individual wrasse varied from 26–46 at water temperatures of 10–12°C and daily food consumption was 1.18–2.72% of body weight.