
Chelsea Wood
Address: Seattle, WA
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Papers by Chelsea Wood
among humanity’s greatest achievements, new research is shedding light on the collateral effects of parasite loss.
Here, we explore a “world without parasites”: a thought experiment for illuminating the ecological roles that parasites
play in ecosystems. While there is robust evidence for the effects of parasites on host individuals (eg affecting
host vital rates), this exercise highlights how little we know about the influence of parasites on communities and
ecosystems (eg altering energy flow through food webs). We present hypotheses for novel, interesting, and general
effects of parasites. These hypotheses are largely untested, and should be considered a springboard for future
research. While many uncertainties exist, the available evidence suggests that a world without parasites would be
very different from the world we know, with effects extending from host individuals to populations, communities,
and even ecosystems.
in fished and unfished areas. Parasite diversity was lower in hosts from fished areas. Larger hosts had a greater abundance of
parasites, suggesting that fishing might reduce the abundance of parasites by selectively removing the largest, most heavily
parasitized individuals. After controlling for size, the effect of fishing on parasite abundance varied according to whether the
host was fished and the parasite’s life cycle. Parasites of unfished hosts were more likely to increase in abundance in response
to fishing than were parasites of fished hosts, possibly due to compensatory increases in the abundance of unfished hosts.
While complex life cycle parasites tended to decline in abundance in response to fishing, directly transmitted parasites
tended to increase. Among complex life cycle parasites, those with fished hosts tended to decline in abundance in response to
fishing, while those with unfished hosts tended to increase. However, among directly transmitted parasites, responses did
not differ between parasites with and without fished hosts. This work suggests that parasite assemblages are likely to change
substantially in composition in increasingly fished ecosystems, and that parasite life history and fishing status of the host are
important in predicting the response of individual parasite species or groups to fishing.
studies have assessed their response to anthropogenic environmental change. Heuristic models
have predicted both increases and decreases in parasite abundance in response to human
disturbance, with empirical support for both. However, most studies focus on one or a few
selected parasite species. Here, we assess the abundance of parasites of seven species of coral
reef fishes collected from three fished and three unfished islands of the Line Islands archipelago
in the central equatorial Pacific. Because we chose fish hosts that spanned different trophic
levels, taxonomic groups, and body sizes, we were able to compare parasite responses across a
broad cross section of the total parasite community in the presence and absence of fishing, a
major human impact on marine ecosystems. We found that overall parasite species richness
was substantially depressed on fished islands, but that the response of parasite abundance
varied among parasite taxa: directly transmitted parasites were significantly more abundant on
fished than on unfished islands, while the reverse was true for trophically transmitted parasites.
This probably arises because trophically transmitted parasites require multiple host species,
some of which are the top predators most sensitive to fishing impacts. The increase in directly
transmitted parasites appeared to be due to fishing-driven compensatory increases in the
abundance of their hosts. Together, these results provide support for the predictions of both
heuristic models, and indicate that the direction of fishing’s impact on parasite abundance is
mediated by parasite traits, notably parasite transmission strategies.
among the ecosystem services yielded by biodiversity.
Lyme disease (LD) is commonly cited as the best example
of the ‘diluting’ effect of biodiversity on disease
transmission, but many studies document the opposite
relationship, showing that human LD risk can increase
with forestation. Here, we unify these divergent perspectives
and find strong evidence for a positive link between
biodiversity and LD at broad spatial scales (urban to
suburban to rural) and equivocal evidence for a negative
link between biodiversity and LD at varying levels of
biodiversity within forests. This finding suggests that,
across zoonotic disease agents, the biodiversity–disease
relationship is scale dependent and complex.
among humanity’s greatest achievements, new research is shedding light on the collateral effects of parasite loss.
Here, we explore a “world without parasites”: a thought experiment for illuminating the ecological roles that parasites
play in ecosystems. While there is robust evidence for the effects of parasites on host individuals (eg affecting
host vital rates), this exercise highlights how little we know about the influence of parasites on communities and
ecosystems (eg altering energy flow through food webs). We present hypotheses for novel, interesting, and general
effects of parasites. These hypotheses are largely untested, and should be considered a springboard for future
research. While many uncertainties exist, the available evidence suggests that a world without parasites would be
very different from the world we know, with effects extending from host individuals to populations, communities,
and even ecosystems.
in fished and unfished areas. Parasite diversity was lower in hosts from fished areas. Larger hosts had a greater abundance of
parasites, suggesting that fishing might reduce the abundance of parasites by selectively removing the largest, most heavily
parasitized individuals. After controlling for size, the effect of fishing on parasite abundance varied according to whether the
host was fished and the parasite’s life cycle. Parasites of unfished hosts were more likely to increase in abundance in response
to fishing than were parasites of fished hosts, possibly due to compensatory increases in the abundance of unfished hosts.
While complex life cycle parasites tended to decline in abundance in response to fishing, directly transmitted parasites
tended to increase. Among complex life cycle parasites, those with fished hosts tended to decline in abundance in response to
fishing, while those with unfished hosts tended to increase. However, among directly transmitted parasites, responses did
not differ between parasites with and without fished hosts. This work suggests that parasite assemblages are likely to change
substantially in composition in increasingly fished ecosystems, and that parasite life history and fishing status of the host are
important in predicting the response of individual parasite species or groups to fishing.
studies have assessed their response to anthropogenic environmental change. Heuristic models
have predicted both increases and decreases in parasite abundance in response to human
disturbance, with empirical support for both. However, most studies focus on one or a few
selected parasite species. Here, we assess the abundance of parasites of seven species of coral
reef fishes collected from three fished and three unfished islands of the Line Islands archipelago
in the central equatorial Pacific. Because we chose fish hosts that spanned different trophic
levels, taxonomic groups, and body sizes, we were able to compare parasite responses across a
broad cross section of the total parasite community in the presence and absence of fishing, a
major human impact on marine ecosystems. We found that overall parasite species richness
was substantially depressed on fished islands, but that the response of parasite abundance
varied among parasite taxa: directly transmitted parasites were significantly more abundant on
fished than on unfished islands, while the reverse was true for trophically transmitted parasites.
This probably arises because trophically transmitted parasites require multiple host species,
some of which are the top predators most sensitive to fishing impacts. The increase in directly
transmitted parasites appeared to be due to fishing-driven compensatory increases in the
abundance of their hosts. Together, these results provide support for the predictions of both
heuristic models, and indicate that the direction of fishing’s impact on parasite abundance is
mediated by parasite traits, notably parasite transmission strategies.
among the ecosystem services yielded by biodiversity.
Lyme disease (LD) is commonly cited as the best example
of the ‘diluting’ effect of biodiversity on disease
transmission, but many studies document the opposite
relationship, showing that human LD risk can increase
with forestation. Here, we unify these divergent perspectives
and find strong evidence for a positive link between
biodiversity and LD at broad spatial scales (urban to
suburban to rural) and equivocal evidence for a negative
link between biodiversity and LD at varying levels of
biodiversity within forests. This finding suggests that,
across zoonotic disease agents, the biodiversity–disease
relationship is scale dependent and complex.