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Definitions of parasitism, considering its potentially opposing effects at different levels of hierarchical organization

Published online by Cambridge University Press:  03 July 2023

Lajos Rózsa*
Affiliation:
Institute of Evolution, Centre for Ecological Research, Budapest H-1121, Hungary Centre for Eco-Epidemiology, National Laboratory for Health Security, Budapest, Hungary
József Garay
Affiliation:
Institute of Evolution, Centre for Ecological Research, Budapest H-1121, Hungary
*
Corresponding author: Lajos Rózsa; Email: [email protected]

Abstract

An annotated synthesis of textbook definitions of parasitism is presented. Most definitions declare parasitism is a long-lasting relationship between individuals of different species harming the hosts. The infection-induced costs are interpreted as diseases in the medical-veterinary literature. Alternatively, evolutionary ecologists interpret it as a reduction of host's fitness (longevity, fertility or both). Authors often assume that such effects decrease host population growth and select for antiparasitic defences, which is not necessarily true because infections may simultaneously express opposite effects at different levels of biological organization. (i) At the cellular level, infection-induced cell growth, longevity and multiplication may yield tumours maladaptive at higher levels. (ii) At the individual level, reduced host longevity, fertility or both are interpreted as disease symptoms or reduced fitness. (iii) Contrary to common sense, the growth rate of infected host lineages may increase in parallel with the individuals' reduced survival and fertility. This is because selection favours not only the production of more offspring but also their faster production. (iv) Finally, infections that reduce host individuals' or lineages' fitness may still increase infected host populations' growth rate in the context of ecological competition. Therefore, differences between parasitism and mutualism may depend on which level of organization one focuses on.

Type
Review Article
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution and reproduction, provided the original article is properly cited.
Copyright
Copyright © The Author(s), 2023. Published by Cambridge University Press

Definitions of parasitism and parasites

Definitions are statements on the meaning of concepts and terms; they are arbitrary tools created to allow for scientific understanding. Definitions need to be operational (applicable), although different purposes often require slightly different definitions of the same concept, and therefore absolute unanimity is not necessarily sought. Nevertheless, certain constancy is still needed to maintain meaningful communication. Definitions that literally mean something other than their intended meaning, or those that are ambiguous in meaning, can be considered erroneous.

A definition of parasitism is essential in teaching parasitology and in textbooks to summarize the general features – so-called ‘laws’ (Poulin, Reference Poulin2007a) – of parasitism, particularly to specify the range of validity of the statements, hypotheses and predictions. Unfortunately, standard textbook definitions of parasitism are highly inconsistent or contradictory (Zelmer, Reference Zelmer1998). Almost all authors agree that parasites harm their hosts by utilizing them as nutrient resources; however, further details can be desperately confusing.

First, a compilation of the main points of the evolutionary-ecological definitions of parasitism is provided below. This is based on the fragmentary definitions in the available literature (Rothschild and Clay, Reference Rothschild and Clay1952; Anderson and May, Reference Anderson and May1978; Price, Reference Price1980; Olsen, Reference Olsen1986; Barnard, Reference Barnard, Barnard and Behnke1990; Rohde, Reference Rohde1993; Clayton and Moore, Reference Clayton, Moore, Clayton and Moore1997; Poulin and Morand, Reference Poulin and Morand2000; Combes, Reference Combes2001; Ebert, Reference Ebert2005; Nunn and Altizer, Reference Nunn and Altizer2006; Poulin, Reference Poulin2007b; Leung and Poulin, Reference Leung and Poulin2008; Martin and Schwab, Reference Martin and Schwab2013; Goater et al., Reference Goater, Goater and Esch2014; Locker and Hofkin, Reference Locker and Hofkin2015; Clayton et al., Reference Clayton, Bush and Johnson2016; Lucius and Poulin, Reference Lucius, Poulin, Lucius, Loos-Frank, Lane, Poulin, Roberts and Grencis2017; Schmid-Hempel, Reference Schmid-Hempel2021; Kaishian et al., Reference Kaishian, Lubbers, De Groot, Schilthuizen and Haelewaters2022). Next, the most crucial criterion is scrutinized; that parasites harm their hosts. Obviously, the usual interpretation of the meaning of ‘damage’ (or ‘cost’) is often contradictory. Finally, no single ‘superior’ definition is proposed to resolve the controversy; only ideas for further consideration and discussion are provided.

Parasitism as a form of symbiosis: a compilation

Symbiosis

Symbiosis is an ecological relationship realized through a direct body-to-body interaction between individuals of separate species, including mutualism and parasitism. Accordingly, intraspecies exploitative interactions do not qualify as parasitism. The dwarf males of the deep-sea anglerfish (Ceratioidei) obtain nutrients from the much larger females, to which they are permanently attached. These males are not parasites, even if they are often called ‘parasitic males’ (Pietsch, Reference Pietsch2005). Likewise, the exploitation of some people by others does not constitute parasitism, although colloquialism sometimes uses the term in this context (see e.g. Lunsing, Reference Lunsing2003), which may seem offensive and unethical to many (Zimmer, Reference Zimmer2000). Further, this criterion excludes associations where the target of exploitation is not a host individual but a group of hosts (like family, colony, etc.). Thus, brood-parasitic birds which exploit host families (Soler, Reference Soler2018), and social parasites which exploit colonies of eusocial insects (Hölldobler and Kwapich, Reference Hölldobler and Kwapich2022) are all excluded, limiting the concept to individual-level exploitative interactions between species (but see also Rothschild and Clay, Reference Rothschild and Clay1952; Barnard, Reference Barnard, Barnard and Behnke1990; Payne, Reference Payne, Clayton and Moore1997).

Intimate relationship

Parasite individuals live in long-standing body-to-body contact with host individuals; inhabiting a single host individual at least for a whole phase of the parasite developmental cycle but often through several life cycles (Price, Reference Price1980; Nunn and Altizer, Reference Nunn and Altizer2006; Poulin, Reference Poulin2007a, Reference Poulin2007b; Locker and Hofkin, Reference Locker and Hofkin2015; Clayton et al., Reference Clayton, Bush and Johnson2016; Lucius and Poulin, Reference Lucius, Poulin, Lucius, Loos-Frank, Lane, Poulin, Roberts and Grencis2017). This long-lasting nature of the bodily contact – colloquially called an ‘intimate relationship’ (Combes, Reference Combes2001) – excludes ‘kleptoparasites’ from animal parasitism and grazers (locusts, ruminants, etc.) from the concept of phytoparasitism. Similarly, it excludes many blood-sucking insects (tabanids, mosquitoes, etc.), ‘micropredators’ in the sense of Poulin (Reference Poulin2011), which have only fleeting contact with their hosts (Lehane, Reference Lehane2005).

Hosts as habitat patches

From the above, it is obvious that the host body acts as a well-defined ‘habitat patch’ for the parasites (and symbionts) (Rothschild and Clay, Reference Rothschild and Clay1952; Anderson and May, Reference Anderson and May1978; Price, Reference Price1980; Rohde, Reference Rohde1993; Clayton and Moore, Reference Clayton, Moore, Clayton and Moore1997; Poulin, Reference Poulin2007b; Locker and Hofkin, Reference Locker and Hofkin2015). This implies that they are relatively small, more numerous, have shorter life cycle and higher reproductive potential, while hosts are large, less numerous, have longer life cycle and lower reproductive potential.

Nutritive relationship

Parasites, just like mutualists, obtain nutrients from the host body and excrete their metabolic by-products (potentially toxic or carcinogenic wastes) there. A similar but non-nutritive interaction is phoresy, which is an exploitation of host mobility and, consequently, host energy resources (Bartlow and Agosta, Reference Bartlow and Agosta2021).

Antagonistic relationship

Parasitism is an antagonistic relationship that damages the host body structure, metabolism or both while benefiting the parasites. In addition, infections often cause further disadvantages, such as exclusion from social (Kurzban and Leary, Reference Kurzban and Leary2001) and sexual relationships (Hamilton and Zuk, Reference Hamilton and Zuk1982), increased chance of predation (Hudson et al., Reference Hudson, Dobson and Newborn1992) and additional co-infections (Sepkowitz, Reference Sepkowitz2002). Contrarily, some parasites may also induce certain beneficial side-effects, e.g. through reduced predation pressure (Hasik et al., Reference Hasik, de Angeli Dutra, Doherty, Duffy, Poulin and Siepielski2023), through negative interactions with other, more virulent infections (Jenner, Reference Jenner1798; Locker and Hofkin, Reference Locker and Hofkin2015), but their net effect on the host is negative by definition. This implies that parasites are dependent on their hosts, while hosts are non-dependent on parasites (Crofton, Reference Crofton1971a; Rohde, Reference Rohde1993). Consequently, parasitism is obligatory for the parasites, but occurrent to the hosts (Ebert, Reference Ebert2005).

Host adaptations to avoid parasite transmission, survival and reproduction

Infections can drastically affect host populations (Hasik and Siepielski, Reference Hasik and Siepielski2022), even though a publication bias may cause mild and symptomless infections to appear much rarer than in reality. The infections' net effects on the hosts can even be so subtle that it is impossible to directly measure, prove or document them. However, these effects may still exert selective pressure on the host populations to evolve adaptive responses to avoid parasite transmission. Due to these host adaptations to avoid infections, transmission from one host to another is a hazardous episode of the parasite life cycle, most often leading to high parasite mortality (Dobson et al., Reference Dobson, Hudson, Lyles and Crawley1992; Combes, Reference Combes2001; Leung and Poulin, Reference Leung and Poulin2008; Locker and Hofkin, Reference Locker and Hofkin2015).

Similarly, host populations frequently also evolve adaptive responses to defend against established infections, to hinder parasite survival, growth and multiplication, providing an indirect verification of the antagonistic nature of the relationship (Poulin, Reference Poulin2007b; Leung and Poulin, Reference Leung and Poulin2008). Despite their counter-adaptations, parasites' vulnerability to host defences typically constitutes a significant cause of their mortality (other than the losses during transmission, see above). Naturally, host nutrient and energy resources allocated to avoidance and defence constitute further parasite-induced metabolic losses.

Since phytophagous arthropods' most effective natural enemies are often species other than the host plants, like parasitoids and predators (Cornell and Hawkins, Reference Cornell and Hawkins1995; Hawkins et al., Reference Hawkins, Cornell and Hochberg1997), this argument does not necessarily apply to them. Therefore, it is advisable to exclude them (most of all species on Earth) from the concept of parasitism (but see also Price, Reference Price1980; Clayton et al., Reference Clayton, Bush and Johnson2016).

Note that host adaptations to avoid or to fight an infection indicate that this symbiont has been parasitic in the past, but not necessarily in the present.

Parasites' distribution across host individuals

Since parasite avoidance and antiparasitic defence are variable traits across hosts, the distribution of parasite individuals across host individuals is aggregated (overdispersed) (Crofton, Reference Crofton1971b; Anderson and May, Reference Anderson and May1978; Clayton and Moore, Reference Clayton, Moore, Clayton and Moore1997). This means that most parasite individuals inhabit a few heavily infected hosts (those with poor avoidance and defence capabilities), while most of the host individuals (those with average or better capabilities) harbour few if any parasites. Contrarily, mutualists often express other types of frequency distributions across host individuals, such as even and polymodal distributions (see e.g. Britayev et al., Reference Britayev, Martin, Krylova, Von Cosel and Aksiuk2007; Elliott et al., Reference Elliott, Chou, Chen, Bloemberg, Bontemps, Martínez-Romero, Velázquez, Young, Sprent and James2009).

The parasitism–mutualism continuum

Contrary to parasites, symbionts which exert positive net effects to the hosts are called mutualists. According to the net costs or benefits caused to the hosts, there is a continuum from parasitism through neutral commensalism to mutualism. Host–symbiont species pairs may shift quite flexibly along this continuum, the nature of their relationship may vary through space and time (Bronstein, Reference Bronstein1994; Leung and Poulin, Reference Leung and Poulin2008; Rózsa and Apari, Reference Rózsa and Apari2012; Lucius and Poulin, Reference Lucius, Poulin, Lucius, Loos-Frank, Lane, Poulin, Roberts and Grencis2017).

Parasites do not usually kill their hosts

Parasites do not usually kill their hosts and therefore, they are not adapted to transmit from dead hosts to new ones. This differentiates them from parasitoids, which kill their host as a prerequisite for successful development and transmission to further host individuals (Rothschild and Clay, Reference Rothschild and Clay1952; Anderson and May, Reference Anderson and May1978; Poulin and Morand, Reference Poulin and Morand2000; Ebert, Reference Ebert2005; Poulin, Reference Poulin2007a, Reference Poulin2007b; Goater et al., Reference Goater, Goater and Esch2014; Locker and Hofkin, Reference Locker and Hofkin2015; Lucius and Poulin, Reference Lucius, Poulin, Lucius, Loos-Frank, Lane, Poulin, Roberts and Grencis2017). According to the different degrees of lethality caused by infections, there is a continuum from non-lethal (more or less mild) parasitism to lethal parasitism (properly called parasitoidism). Host–symbiont species pairs may shift quite flexibly along this continuum, the nature of their relationship may vary through space and time. Taking trophically transmitted parasites as an example, they often manipulate intermediate host behaviour to increase predation by the definitive host. This means that they kill their hosts indirectly through a predator, the frequency and effectiveness of which can vary between species.

Taxonomic scope of parasitism

Finally, several authors specify a taxonomic scope of parasitism for historical and practical reasons (Poulin, Reference Poulin2007a, Reference Poulin2007b; Locker and Hofkin, Reference Locker and Hofkin2015). Some authors delimit the concept to include only animals and ‘animal-like’ (eukaryotic and heterotrophic) protists that parasitize animals (e.g. Goater et al., Reference Goater, Goater and Esch2014). Others include all types of microbes, plants and fungi, both as hosts and as parasites. Finally, some authors include even suborganismal entities – like viruses and macromolecules, such as nucleic acid or protein strands (RNA, DNA, prions) – into the concept of parasitism, setting the maximum of a taxonomical domain (Combes, Reference Combes2001; Lucius and Poulin, Reference Lucius, Poulin, Lucius, Loos-Frank, Lane, Poulin, Roberts and Grencis2017).

Infection-induced harms across 4 levels of hierarchical organization

Whatever definition is preferred, the notion that parasites exert a net harmful effect on their hosts is a foremost characteristic of host–parasite relationships. From ancient times, this feature contributed much to the negative emotions about parasites (Zimmer, Reference Zimmer2000; Kaishian et al., Reference Kaishian, Lubbers, De Groot, Schilthuizen and Haelewaters2022). Contrarily, mutualists are defined by the net beneficial effect they exert on infected hosts.

It is traditional in the human and veterinary medical literature to treat infection-induced harms as a synonymy of parasites' pathogenicity, i.e. their capacity to produce disease, thus increasing the host population's morbidity and mortality rates (Vihinen, Reference Vihinen2017). However, at the dawn of the science of parasite ecology and evolution, it became evident that practically all large-bodied organisms are infected by some (and often by several) species of micro- and macroparasites (i.e. species that are usually thought of as parasites) most often without ever developing symptoms of any disease. Thus, the notions of morbidity and disease had to be replaced by an evolutionary-ecological concept of the harms caused by parasites. For this reason, Anderson (Reference Anderson1978) and Anderson and May (Reference Anderson and May1978) opened a new avenue of definitions by proposing that a parasite causes an ‘inducement of host mortalities and/or reduction in host reproductive potential’ and, thus, exerts a ‘detrimental effect on the intrinsic growth rate of its host population’. The authors defined both birth and death rates as events/host/unit of time. Note that individual and population-level harms of infection are mentioned as if they were equal.

However, this idea ignores the nested hierarchical nature of the biological organization, which is a fundamental feature of life (Szathmáry and Maynard Smith, Reference Szathmáry and Maynard Smith1995). Therefore, the crucial question is whether or not infection-induced effects at different levels of the biological hierarchy are necessarily consistent with each other.

Level 1: host cells

A multicellular organism's survival and reproductive success depend on its ability to regulate its cells' growth, survival and reproduction. Cellular infections can modify all these 3 components. First, programmed cell growth can be obstructed by various protist and fungal infections, most notably by Microsporidia, occurring predominantly in fish hosts. Infected cells grow into vast masses of parasites packed within a single host cell called xenoma (Lom and Dyková, Reference Lom and Dyková2005). Second, programmed cell death (apoptosis) and controlled cell division are also essential. Whenever cell division runs amok in an unregulated manner, a malignant tumour develops, threatening the very existence of the multicellular individuals. Taking the population of the USA as an example, approximately 3–4% of all cancer cases are attributable to the most common carcinogenic infections like Helicobacter pylori, hepatitis B virus, hepatitis C virus, human herpes virus type 8, human immunodeficiency virus or human papillomavirus (Islami et al., Reference Islami, Goding Sauer, Miller, Siegel, Fedewa, Jacobs, McCullough, Patel, Ma, Soerjomataram, Flanders, Brawley, Gapstur and Jemal2018). Evidently, infection-induced increase in cellular growth, survival and reproduction reduces the survival and reproduction of the multicellular host organism.

Level 2: host individuals

For obvious reasons, medical and veterinary scientists focus their interest on diseases. Symptoms define diseases, and – understandably – infected hosts' reduced lifespan and fertility are among the most obvious symptoms. Contrarily, health is characterized by a long and fertile life. Therefore, infections that increase host longevity, fertility or both are classified as mutualists. Similarly, in the evolutionary-ecological literature, a parasite-induced reduction of host lifetime reproductive success (LRS) is also interpreted as indisputable evidence for parasitism by thousands of research articles (see e.g. Herre, Reference Herre1993; Lipsitsch et al., Reference Lipsitsch, Siller and Nowak1996; van Dijk and De Baets, Reference van Dijk, De Baets, De Baets and Huntley2021).

Level 3: host lineages

Lineages are comprised of host individuals linked by genetic inheritance along the parent–offspring relationships. Lineages are usually not regarded as a distinct level of biological organization; however, ever since Darwin (Reference Darwin1859) they represent units of selection (see e.g. Garay et al., Reference Garay, Varga, Gámez and Cabello2016; Nunney, Reference Nunney and Keller2019, Krishnan et al., Reference Krishnan, Rózsa, Szilágyi and Garay2023). In modern days, the concept of multilevel selection posits that selection occurs in parallel at various levels in the hierarchy of biological organization (Wade et al., Reference Wade, Wilson, Goodnight, Taylor, Bar-Yam, de Aguiar, Stacey, Werfel, Hoelzer, Brodie, Fields, Breden, Linksvayer, Fletcher, Richerson, Bever, Van Dyken and Zee2010). Following these views, lineages are treated here as one of the parallel levels of selection.

For sake of simplicity, we consider only parthenogenetic (asexual) host lineages. At first glance, this appears to be nonsense because a symbiont which transmits exclusively along mother-to-daughter routes in a parthenogenetic host population necessarily tends to a mutualist way of life. Otherwise, if it reduces host fitness, then it will be lost from the host population (Fine, Reference Fine1975; Frank, Reference Frank1996). In this case, however, the growth rates of infected and non-infected host lineages must be compared. For this purpose, it is not necessary to presume that parasites or mutualists are transmitted along these lineages; instead, the genetic predispositions of hosts (such as genes regulating the immune system) are transmitted along the parent–offspring relationships. Thus, whatever transmission route (horizontal or vertical) is used by parasites, it is the host's infection state (infected or uninfected) that is inherited along the lineages.

By definition, parasites are expected to reduce the growth rate of infected lineages compared to uninfected ones, while mutualists are expected to exert the opposite effect. Readers may intuitively assume that infections which decrease the host individuals' survival and reproduction necessarily decrease the fitness of infected host lineages too – which is not necessarily true. Fitness is a term with several subtly different meanings (Orr, Reference Orr2009). Generally speaking, it is the expected contribution of alleles, genotypes or organisms to future generations relative to the other alternative alleles, genotypes or organisms in the population (Stearns, Reference Stearns1992; Pásztor et al., Reference Pásztor, Botta-Dukát, Magyar, Czárán and Meszéna2016). Let us consider a hypothetical example. Part of the population harbours an infection that halves both longevity and fertility of infected hosts. Say, uninfected hosts complete their life cycle in 2 years and produce 4 offspring at the end of their life, while infected hosts live only for 1 year and produce only 2 offspring at the end of their life. Thus, the annual growth of the uninfected host lineage is 1, 1, 4, 4, 16 through 5 years, while that of the infected hosts is 1, 2, 4, 8, 16 through the same period. In this imaginary case, infection halves both the longevity and LRS of host individuals, while it does not change the fitness (growth rate) of infected lineages. Logically, this symbiont should be classified as a neutral commensal. Under the same simplistic circumstances, a symbiont that doubles the lifespan and fertility of infected hosts would also not qualify as a mutualist.

Real-life host populations, however, most often have overlapping generations; thus, the combined effects of changes in longevity and fecundity are more challenging to assess. Nevertheless, it is easy to construct hypothetical models in which reducing host lifespan, reproduction or both comes together with increasing host lineage growth. Examples are provided for infections that (i) reduce host longevity, do not affect LRS, but increase host lineage growth (Box 1), (ii) do not affect mortality, reduce LRS, but increase host lineage growth (Box 2), (iii) reduce both host lifespan and LRS, but increase host lineage growth (Box 3). In the last hypothetical example, not only host lifespan and LRS, but also the mean annual fecundity is unchanged, while the host lineage growth increases (Box 4). Note that all these counter-intuitive effects are based on the fact that selection favours not only the greater fecundity but also, the faster speed of producing offspring (Brommer et al., Reference Brommer, Merilä and Kokko2002), as visualized in Fig. 1.

Box 1. Increasing host mortality may increase host lineage growth

In population ecology, Leslie matrices are discrete-time, age-structured demographic models of populations with overlapping generations. They describe the multiplication of female individuals only. Let us consider a simple life history model where:

  • the lifespan of the uninfected hosts is 3 years, and the 1st year juveniles do not multiply,

  • the survival rate in the t-th year age is denoted by ω t,

  • the average fecundity in the t-th year is denoted by α t,

thus the lifetime reproductive success (LRS) is ω 1α 2 + ω 1ω 2α 3 (a host can reach the 2nd year with probability ω 1 when it multiplies by α 2, and the 3rd year with probability ω 1ω 2when it multiplies α 3).

Using this notation, the Leslie matrix reads as

$$\left({\matrix{ 0 & {\alpha_2} & {\alpha_3} \cr {\omega_1} & 0 & 0 \cr 0 & {\omega_2} & 0 \cr } } \right).$$

In this model, there are 3 ways how a symbiont might affect the infected host population:

  • decrease or increase the life span,

  • decrease or increase at least one survival rate,

  • decrease or increase at least one fecundity rate.

The long-term growth rate (R 0) of host lineages can be determined as the asymptotic growth rate (the dominant, positive eigenvalue of the Leslie matrix) corresponding to the stable age distribution (Caswell, Reference Caswell2001).

Using these notations, consider an infection that increases host mortality, does not affect LRS, but increases host lineage growth. Let us compare the Leslie matrices of infected vs uninfected host lineages of a hypothetical population. We assume that not the parasites themselves, but the hosts' state of being infected vs uninfected is transmitted through generations.

Uninfected hosts, LRS: 1 × 1 + 1 × 1 × 3 = 4

$$\left({\matrix{ 0 & 1 & 3 \cr 1 & 0 & 0 \cr 0 & 1 & 0 \cr } } \right)$$

Infected hosts, LRS: 1 × 4 = 4

$$\left({\matrix{ 0 & 4 \cr 1 & 0 \cr } } \right)$$

The long-term growth rate of the uninfected lineage is R 0 ≈ 1.67, and that of the infected lineage is R 0 = 2.

Box 2. Reducing host LRS may increase host lineage growth

Using the same notations and assumptions as above, consider the following example:

Uninfected host, LRS: 1 × 1 + 1 × 1 × 5 = 6

$$\left({\matrix{ 0 & 1 & 5 \cr 1 & 0 & 0 \cr 0 & 1 & 0 \cr } } \right)$$

Infected host, LRS: 1 × 3 + 1 × 1 × 2 = 5

$$\left({\matrix{ 0 & 3 & 2 \cr 1 & 0 & 0 \cr 0 & 1 & 0 \cr } } \right)$$

The long-term growth rate of the uninfected hosts is R 0 ≈ 1.90, and that of the infected hosts is R 0 = 2.00.

Box 3. Reducing host lifespan and LRS may increase host lineage growth

Using the same notations and assumptions as above:

Uninfected host, LRS: 1 × 1 + 1 × 0.55 × 2 = 2.1

$$\left({\matrix{ 0 & 1 & 2 \cr 1 & 0 & 0 \cr 0 & {0.55} & 0 \cr } } \right)$$

Infected host, LRS: LRS = 1 × 2 = 2

$$\left({\matrix{ 0 & 2 \cr 1 & 0 \cr } } \right)$$

The long-term growth rate of the uninfected lineage is R 0 ≈ 1.35, and that of the infected lineage is R 0 ≈ 1.41.

Box 4. Host lifespan, LRS and mean annual fecundity are unchanged, but host lineage growth increases

Using the same notations and assumptions as above:

Uninfected host, LRS: 1 × 1 + 1 × 1 × 2 = 3

$$\left({\matrix{ 0 & 1 & 2 \cr 1 & 0 & 0 \cr 0 & 1 & 0 \cr } } \right)$$

Infected host, LRS: 1 × 2 + 1 × 1 × 1 = 3

$$\left({\matrix{ 0 & 2 & 1 \cr 1 & 0 & 0 \cr 0 & 1 & 0 \cr } } \right)$$

The long-term growth rate of the uninfected hosts is R 0 ≈ 1.52, and that of the infected hosts is R 0 ≈ 1.62 (see also Fig. 1).

Figure 1. An infection that does not change host lifespan, lifetime reproductive success (LRS) or mean annual fecundity may still increase or decrease the growth rate of host lineages. Representation of 2 hypothetical parthenogenetic host lineages, where individuals' longevity is 3 years, there is no reproduction in the 1st year, and a total of 3 offspring are produced during the 2nd and 3rd years. Above, individuals breed less intensively in the 2nd year and more intensively in the 3rd year, which is reversed below. Shifting the reproduction peak to an earlier period in the life cycle increases growth rate, even though population dynamic indices (longevity, LRS, annual mortality and fecundity rates) are equal. Solid lines represent the survival of individuals to the following year, and dotted lines represent reproduction. Darker circles represent later generations than lighter ones (see also Box 4).

To the best of our knowledge, no one has raised these points before, so previous studies have never interpreted the differences between parasite-infected and non-infected host lineages along these lines. However, the contradictory results of some studies seem to suggest that similar phenomena may occasionally occur. For example, fungal endophytes increase fecundity in the grass Agrostis hyemalis at the expense – or benefit? – of reducing its longevity (Yule et al., Reference Yule, Miller and Rudgers2013). Toxoplasma gondii, a widespread infection in rodents and humans, increase predation pressure (Berdoy et al., Reference Berdoy, Webster and Macdonald1995) and traffic accidents (Gohardehi et al., Reference Gohardehi, Sharif, Sarvi, Moosazadeh, Alizadeh-Navaei, Hosseini, Amouei, Pagheh, Sadeghi and Daryani2018) of infected hosts while, on the other hand, makes them sexually more attractive potentially increasing their reproductive success (Dass et al., Reference Dass, Vasudevan, Dutta, Soh, Sapolsky and Vyas2011; Borráz-León et al., Reference Borráz-León, Rantala, Krams, Cerda-Molina and Contreras-Garduño2022). We cannot quantify the combined fitness effects of reduced lifespan and (presumably) increased reproductive success of infected hosts; however, host adaptations to combat Toxoplasma infections indicate that it is unfavourable at the lineage level.

Level 4: host populations

We usually expect parasite infections to decrease and mutualist infections to increase the host population growth rate (Anderson and May, Reference Anderson and May1978). In real life, however, host populations are embedded in ecological communities formed by a network of several interspecific relationships. Relationships other than the host–parasite relationship in focus may influence the actual parasite-induced harm or benefit to the host population. Thus, certain symbionts that decrease host fitness at the former levels may still increase host population growth rate.

Looking at a multispecies community, successfully invading populations may benefit from hosting pathogens and transmitting them to endemic competitor populations (McNeill, Reference McNeill1976). ‘McNeill's Rule’, i.e. a pathogen-mediated negative interaction between host species (or populations) is also called ‘parasite-mediated competition’ or ‘apparent competition’ or ‘novel weapon hypothesis’ in the parasitological literature (Hudson and Greenman, Reference Hudson and Greenman1998; Ricklefs, Reference Ricklefs2010; Vilcinskas, Reference Vilcinskas2015). For instance, in human history, the spillover of smallpox and measles from the colonizing European populations decreased the competitive abilities of native populations (McNeill, Reference McNeill1976; Diamond, Reference Diamond1998). Similarly, apparent competition mediated via shared parasites contributes to the invasion success of introduced exotic gamebirds (Tompkins et al., Reference Tompkins, Draycott and Hudson2002a), crayfish (Small and Pagenkopp, Reference Small and Pagenkopp2011) and squirrels (Tompkins et al., Reference Tompkins, Sainsbury, Nettleton, Buxton and Gurnell2002b). This phenomenon is caused by the differential virulence (low in the coevolved invasive species and high in the naive indigenous hosts) that yields a parasite-mediated competitive advantage of the invasive population. Thus, an infection-induced reduction of individual fitness within the invasive host population comes together with the increased competitive success of this population.

Examples of the opposite scenario may also occur, i.e. symbionts that are mutualistic at the individual or lineage level but harmful at the population level. We suspect that Wolbachia infections of some insect populations may exemplify this case. Some strains of Wolbachia induce parthenogenesis in the infected insects, often making whole populations or species parthenogenetic (Knight, Reference Knight2001). Switching to parthenogenesis likely increases individual and lineage multiplication rates since all the metabolic and genetic costs of sex are spared. However, parthenogenetic reproduction is a self-destructive strategy; asexual populations and species are more likely to go extinct in the long run (Moreira et al., Reference Moreira, Fonseca and Rojas2021).

Discussion

In this review, we first put the pieces of the textbooks' fragmentary descriptions together to compile an annotated definition of parasitism and parasites. Points 1–4 of this definition outline symbiosis (including both mutualism and parasitism) as a long-lasting, nutritive, body-to-body relationship between 2 individuals belonging to separate species. The 5th point posits that parasitism – unlike mutualism – is harmful for the host and beneficial for the parasite individual. The next 2 points are evolutionary-ecological consequences of this asymmetry postulating that hosts are adapted to avoid infections and to fight established ones, which results in an aggregated distribution of parasites. Hence, the antagonistic nature of this relationship is crucial in defining parasitism and parasites.

However, whether a relationship is mutually beneficial (mutualism) or harmful to one of the partners (parasitism) depends on which level of biological organization we focus on. Therefore, we overviewed the infection-induced harms (also known as costs, expenses, losses or damages) to the hosts at different levels. We have shown that negative effects expressed at a given hierarchy level can accompany positive effects at another hierarchy level. We do not claim that infections' opposing effects at different levels of organization would be a common phenomenon, neither that it would often cause problems in defining parasitism and parasites. We simply say that these phenomena are worth thinking about.

The fact that certain cellular infections can increase host cell growth, survival and reproduction, and thus give rise to malignant tumours fatal to host individuals is commonplace medical knowledge. In this case, an increase in the fitness of the infected cell line causes a decrease in the fitness of the host individual. This apparent contradiction does not cause any confusion in the definition of parasitism because the decrease in fitness is traditionally interpreted for individuals.

At the same time, the parasitological literature does not recognize the fact that a reduction in the lifespan of an individual does not necessarily mean a cost (harm) to the infected host lineages. This is because medical and veterinary scientists necessarily apply a ‘health-or-disease’ perspective, and living a longer life seems healthier. Contrarily, however, assuming LRS is equal, faster life cycle completion is adaptive compared to a slower and longer life. Thus, comparing the adaptive success of host lineages, higher mortality can outcompete lower mortality.

Similarly, higher LRS seems healthier than lower. However, assuming longevity is equal, we conclude that the pure number and quality of descendants are not the only factors influencing adaptive success. Selection also favours the speed of reproduction, thus an infection that makes hosts breeding in an earlier phase of the life cycle may be advantageous at the level of host lineages. For this reason, lineages with higher LRS can be outcompeted by lineages with higher long-term growth rate (R 0) (Garay et al., Reference Garay, Varga, Gámez and Cabello2016).

Although we do not deny the possibility of multilevel selection, we believe that the vast majority of antiparasitic adaptations (point 6 of the definition above) arise due to selection occurring at the lineage level. Admittedly, this is an ‘orthodox Darwinian’ viewpoint. The most obvious difference between the medical-veterinary (focusing on individual fitness) and the orthodox Darwinian (focusing on lineage fitness) perspectives lies in evaluating the significance of changes in host lifespan. From the former perspective, the reduced lifespan of the host (indicated by increased mortality) is the cost of infection; from the latter perspective (all else being equal), the reduced lifespan represents a faster life cycle, i.e. an advantage.

We have primarily used hypothetical examples to illustrate the complex way in which longevity, the number of descendants and the timing of their production determine the adaptive success or failure of lineages, with a few real-life examples also mentioned.

Finally, the fact that invasive host populations may benefit from carrying pathogens (even if they are harmful at the individual and lineage levels) in the context of ecological competition has been known for ages. Ironically, this ecological hypothesis was first introduced by a historian (McNeill, Reference McNeill1976) who recognized the importance of pathogen spillover from European invaders to indigenous people during the colonization of the Third World. Unfortunately, parasite ecologists still have trouble distinguishing between McNeill's rule (which postulates that the presence of certain infections is beneficial to invasive populations) and the Enemy Release Hypothesis (which postulates the opposite; that invasive populations benefit from the absence of certain infections). Rózsa et al. (Reference Rózsa, Tryjanowski, Vas, Morand, Krasnov and Littlewood2015) argued that these 2 hypotheses are not mutually exclusive but rather they tend to co-occur with 2 different types of invasions (invasions by small and isolated populations established by a few pioneers vs mass invasions). Nevertheless, ecologists still tend to treat McNeill's rule as a peculiarity, an exceptional situation when parasites confer benefits to the host populations. Probably due to the dominance of the traditional individual-focused viewpoint, community ecologists have not yet asked why to categorize these symbionts as parasites.

Conclusion

Overall, we have shown that definitions of parasites and parasitism rely (among others) on the antagonistic nature of this relationship. However, the harms and benefits caused by parasites may be opposing across 4 different levels of organizational hierarchy making the differentiation between parasitism and mutualism vaguer than formerly thought. We believe that medical and veterinary parasitologists continue to focus on host individuals. Evolutionary biologists go on focusing on host lineages, because this is the hierarchical level where selection most effectively yields in adaptations. Finally, community ecologists are interested in the dynamics of host populations. Clarifying the differences between these viewpoints may hopefully help to increase understanding in communication across these different fields of science.

Data availability statement

No additional data are associated with this study.

Acknowledgements

We are grateful to Beáta Oborny, János Podani and anonymous reviewers for useful comments on earlier drafts of the manuscript.

Author contributions

Both authors contributed equally to the conceptualization of this review article. J. G. wrote the Leslie matrices to model lineage growth, and L. R. wrote the article text.

Financial support

L. R.'s work was supported by the National Research, Development, and Innovation Office of Hungary (RRF-2.3.1-21-2022-00006) and the National Research, Development, and Innovation Fund of Hungary (K143622).

Competing interest

None.

Ethical standards

Not applicable.

References

Anderson, RM (1978) The regulation of host population growth by parasitic species. Parasitology 76, 119157.CrossRefGoogle ScholarPubMed
Anderson, RM and May, RM (1978) Regulation and stability of host-parasite population interactions. Journal of Animal Ecology 47, 219247.CrossRefGoogle Scholar
Barnard, CJ (1990) Parasitic relationships. In Barnard, CJ and Behnke, JM (eds), Parasitism and Host Behaviour. Abingdon, UK: Taylor & Francis, pp. 133.CrossRefGoogle Scholar
Bartlow, AW and Agosta, SJ (2021) Phoresy in animals: review and synthesis of a common but understudied mode of dispersal. Biological Reviews 96, 223246.CrossRefGoogle ScholarPubMed
Berdoy, M, Webster, JP and Macdonald, DW (1995) The manipulation of rat behaviour by Toxoplasma gondii. Mammalia 59, 605613.CrossRefGoogle Scholar
Borráz-León, JI, Rantala, MJ, Krams, IA, Cerda-Molina, AL and Contreras-Garduño, J (2022) Are Toxoplasma-infected subjects more attractive, symmetrical, or healthier than non-infected ones? Evidence from subjective and objective measurements. PeerJ 10, e13122.CrossRefGoogle ScholarPubMed
Britayev, TA, Martin, D, Krylova, EM, Von Cosel, R and Aksiuk, TS (2007) Life-history traits of the symbiotic scale-worm Branchipolynoe seepensis and its relationships with host mussels of the genus Bathymodiolus from hydrothermal vents. Marine Ecology 28, 3648.CrossRefGoogle Scholar
Brommer, JE, Merilä, J and Kokko, H (2002) Reproductive timing and individual fitness. Ecology Letters 5, 802810.CrossRefGoogle Scholar
Bronstein, JL (1994) Conditional outcomes in mutualistic interactions. Trends in Ecology & Evolution 9, 214217.Google ScholarPubMed
Caswell, H (2001) Matrix Population Models: Construction, Analysis, and Interpretation. Sunderland, MA: Sinauer Associates, ISBN: 0878930965.Google Scholar
Clayton, DH and Moore, J (1997) Introduction. In Clayton, DH and Moore, J (eds), Host-Parasite Evolution: General Principles and Avian Models. Oxford, UK: Oxford University Press, pp. 16.Google Scholar
Clayton, DH, Bush, SE and Johnson, KP (2016) Coevolution of Life on Hosts: Integrating Ecology and History. Chicago, IL: University of Chicago Press, ISBN: 022630227X.Google Scholar
Combes, C (2001) Parasitism, the Ecology and Evolution of Intimate Interactions. Chicago, IL: University of Chicago Press, ISBN: 0226114465.Google Scholar
Cornell, HV and Hawkins, BA (1995) Survival patterns and mortality sources of herbivorous insects: some demographic trends. American Naturalist 145, 563593.CrossRefGoogle Scholar
Crofton, HD (1971a) A model of host-parasite relationships. Parasitology 63, 343364.CrossRefGoogle Scholar
Crofton, HD (1971b) A quantitative approach to parasitism. Parasitology 62, 179193.CrossRefGoogle Scholar
Darwin, C (1859) The Origin of Species by Means of Natural Selection. London, UK: Murray J.Google Scholar
Dass, SAH, Vasudevan, A, Dutta, D, Soh, LJT, Sapolsky, RM and Vyas, A (2011) Protozoan parasite Toxoplasma gondii manipulates mate choice in rats by enhancing attractiveness of males. PLoS ONE 6, e27229.Google ScholarPubMed
Diamond, J (1998) Guns, Germs and Steel: A Short History of Everybody for the Last 13000 Years. New York City, NY: Vintage Books, ISBN: 0099302780.Google Scholar
Dobson, AP, Hudson, PJ and Lyles, AM (1992) Macroparasites: it's a wormy world. In Crawley, MJ (ed.), Natural Enemies. The Population Biology of Predators, Parasites and Diseases. Hoboken, NJ: Blackwell Scientific, pp. 329348.Google Scholar
Ebert, D (2005) Ecology, Epidemiology, and Evolution of Parasitism in Daphnia. Bethesda, MD: National Center for Biotechnology Information, ISBN: 1932811060.Google Scholar
Elliott, GN, Chou, JH, Chen, WM, Bloemberg, GV, Bontemps, C, Martínez-Romero, E, Velázquez, E, Young, JPW, Sprent, JI and James, EK (2009) Burkholderia spp. are the most competitive symbionts of Mimosa, particularly under N-limited conditions. Environmental Microbiology 11, 762778.CrossRefGoogle ScholarPubMed
Fine, FEM (1975) Vectors and vertical transmission: an epidemiological perspective. Annals of the New York Academy of Sciences 266, 173194.CrossRefGoogle Scholar
Frank, SA (1996) Models of parasite virulence. Quarterly Review of Biology 71, 3778.Google ScholarPubMed
Garay, J, Varga, Z, Gámez, M and Cabello, T (2016) Sib cannibalism can be adaptive for kin. Ecological Modelling 334, 5159.CrossRefGoogle Scholar
Goater, TM, Goater, CP and Esch, GW (2014) Parasitism: The Diversity and Ecology of Animal Parasites. Cambridge, UK: Cambridge University Press, ISBN: 0521190282.Google Scholar
Gohardehi, S, Sharif, M, Sarvi, S, Moosazadeh, M, Alizadeh-Navaei, R, Hosseini, SA, Amouei, A, Pagheh, A, Sadeghi, M and Daryani, A (2018) The potential risk of toxoplasmosis for traffic accidents: a systematic review and meta-analysis. Experimental Parasitology 191, 1924.CrossRefGoogle ScholarPubMed
Hamilton, WD and Zuk, M (1982) Heritable true fitness and bright birds: a role for parasites? Science 218, 384387.CrossRefGoogle Scholar
Hasik, AZ and Siepielski, AM (2022) Parasitism shapes selection by drastically reducing host fitness and increasing host fitness variation. Biology Letters 18, 20220323.CrossRefGoogle ScholarPubMed
Hasik, AZ, de Angeli Dutra, D, Doherty, JF, Duffy, MA, Poulin, R and Siepielski, AM (2023) Resetting our expectations for parasites and their effects on species interactions: a meta-analysis. Ecology Letters 26, 184199.CrossRefGoogle ScholarPubMed
Hawkins, BA, Cornell, HV and Hochberg, ME (1997) Predators, parasitoids, and pathogens as mortality agents in phytophagous insect populations. Ecology 78, 21452152.CrossRefGoogle Scholar
Herre, EA (1993) Population structure and the evolution of virulence in Nematode parasites of Fig Wasps. Science 259, 14421445.CrossRefGoogle ScholarPubMed
Hölldobler, B and Kwapich, CL (2022) The Guests of Ants: How Myrmecophiles Interact with Their Hosts. Cambridge, MA: Harvard University Press, ISBN: 0674276442.Google Scholar
Hudson, P and Greenman, J (1998) Competition mediated by parasites: biological and theoretical progress. Trends in Ecology & Evolution 13, 387390.CrossRefGoogle ScholarPubMed
Hudson, PJ, Dobson, AP and Newborn, D (1992) Do parasites make prey vulnerable to predation? Red Grouse and parasites. Journal of Animal Ecology 61, 681692.CrossRefGoogle Scholar
Islami, F, Goding Sauer, A, Miller, KD, Siegel, RL, Fedewa, SA, Jacobs, EJ, McCullough, ML, Patel, AV, Ma, J, Soerjomataram, I, Flanders, WD, Brawley, OW, Gapstur, SM and Jemal, A (2018) Proportion and number of cancer cases and deaths attributable to potentially modifiable risk factors in the United States. CA-A Cancer Journal for Clinicians 68, 3154.CrossRefGoogle ScholarPubMed
Jenner, E (1798) An Inquiry into the Causes and Effects of the Variolae Vaccinae: a Disease Discovered in Some of the Western Counties of England, Particularly Gloucestershire, and Known by the Name of the Cow Pox. London, UK: Sampson Low.Google Scholar
Kaishian, P, Lubbers, M, De Groot, MD, Schilthuizen, M and Haelewaters, D (2022) Definitions of parasites and pathogens through time. Authorea Preprints. doi: 10.22541/au.165712662.22738369/v1Google Scholar
Knight, J (2001) Meet the Herod bug. Nature 412, 1214.CrossRefGoogle ScholarPubMed
Krishnan, N, Rózsa, L, Szilágyi, A and Garay, J (2023) Coevolutionary stability of host-symbiont systems with mixed-mode transmission. bioRxiv. doi: 10.1101/2023.02.06.527336CrossRefGoogle Scholar
Kurzban, R and Leary, MR (2001) Evolutionary origins of stigmatization: the functions of social exclusion. Psychological Bulletin 123, 187208.CrossRefGoogle Scholar
Lehane, M (2005) The Biology of Blood-Sucking in Insects. Cambridge, UK: Cambridge University Press, ISBN: 0521836085.CrossRefGoogle Scholar
Leung, TLF and Poulin, R (2008) Parasitism, commensalism, and mutualism: exploring the many shades of symbioses. Vie et Milieu-Life and Environment 58, 107115.Google Scholar
Lipsitsch, M, Siller, S and Nowak, MA (1996) The evolution of virulence in pathogens with vertical and horizontal transmission. Evolution 50, 17291741.Google Scholar
Locker, ES and Hofkin, BV (2015) Parasitology: A Conceptual Approach. Abingdon, UK: Taylor & Francis, ISBN: 1317407725.CrossRefGoogle Scholar
Lom, J and Dyková, I (2005) Microsporidian xenomas in fish seen in wider perspective. Folia Parasitologica 52, 6981.CrossRefGoogle ScholarPubMed
Lucius, R and Poulin, R (2017) General aspects of parasite biology. In Lucius, R, Loos-Frank, B, Lane, RP, Poulin, R, Roberts, C and Grencis, RK (eds), The Biology of Parasites. New York City, NY: John Wiley & Sons, pp. 194.Google Scholar
Lunsing, W (2003) ‘Parasite’ and ‘non-parasite’ singles: Japanese journalists and scholars taking positions. Social Science Japan Journal 6, 261265.CrossRefGoogle Scholar
Martin, BD and Schwab, E (2013) Current usage of symbiosis and associated terminology. International Journal of Biology 5, 3245.Google Scholar
McNeill, WH (1976) Plagues and People. New York City, USA: Anchor Press, ISBN: 0385121229.Google Scholar
Moreira, MO, Fonseca, C and Rojas, D (2021) Parthenogenesis is self-destructive for scaled reptiles. Biology Letters 17, 20210006.CrossRefGoogle ScholarPubMed
Nunn, CL and Altizer, S (2006) Infectious Diseases in Primates: Behavior, Ecology and Evolution. Oxford, UK: Oxford University Press, ISBN: 0198565852.CrossRefGoogle Scholar
Nunney, L (2019) Lineage selection: natural selection for long-term benefit. In Keller, L (ed.), Levels of Selection in Evolution. Princeton, NJ: Princeton University Press, pp. 238252.CrossRefGoogle Scholar
Olsen, OW (1986) Animal Parasites: Their Life Cycles and Ecology. New York City, NY: Dover Publications, ISBN: 0486651266.Google Scholar
Orr, HA (2009) Fitness and its role in evolutionary genetics. Nature Reviews Genetics 10, 531539.CrossRefGoogle ScholarPubMed
Pásztor, L, Botta-Dukát, Z, Magyar, G, Czárán, T and Meszéna, G (2016) Theory-based Ecology: A Darwinian Approach. Oxford, UK: Oxford University Press, ISBN: 0199577854.CrossRefGoogle Scholar
Payne, RB (1997) Avian brood parasitism. In Clayton, DH and Moore, J (eds), Host-parasite Evolution: General Principles and Avian Models. Oxford, UK: Oxford University Press, pp. 338369.Google Scholar
Pietsch, T (2005) Dimorphism, parasitism, and sex revisited: modes of reproduction among deep-sea ceratioid anglerfishes (Teleostei: Lophiiformes). Ichthyological Research 52, 207236.CrossRefGoogle Scholar
Poulin, R (2007a) Are there general laws in parasite ecology? Parasitology 134, 763776.CrossRefGoogle ScholarPubMed
Poulin, R (2007b) Evolutionary Ecology of Parasites. Princeton, NJ: Princeton University Press, ISBN: 9780691120850.CrossRefGoogle Scholar
Poulin, R (2011) The many roads to parasitism: a tale of convergence. Advances in Parasitology 74, 140.CrossRefGoogle ScholarPubMed
Poulin, R and Morand, S (2000) The diversity of parasites. Quarterly Review of Biology 75, 277293.CrossRefGoogle ScholarPubMed
Price, PW (1980) Evolutionary Biology of Parasites. Princeton, NJ: Princeton University Press, ISBN: 069108257X.Google ScholarPubMed
Ricklefs, RE (2010) Host-pathogen coevolution, secondary sympatry and species diversification. Philosophical Transactions of the Royal Society B-Biological Sciences 365, 11391147.CrossRefGoogle ScholarPubMed
Rohde, K (1993) Ecology of Marine Parasites. Wallingford, UK: CAB International, ISBN: 0851988458.CrossRefGoogle Scholar
Rothschild, M and Clay, T (1952) Fleas, Flukes and Cuckoos. A Study of Bird Parasites. London, UK: Collins.Google Scholar
Rózsa, L and Apari, P (2012) Why infest the loved ones – inherent human behaviour indicates former mutualism with head lice. Parasitology 139, 696700.CrossRefGoogle ScholarPubMed
Rózsa, L, Tryjanowski, P and Vas, Z (2015) Under the changing climate: how shifting geographic distributions and sexual selection shape parasite diversification. In Morand, S, Krasnov, B and Littlewood, T (eds), Parasite Diversity and Diversification: Evolutionary Ecology Meets Phylogenetics. Cambridge, UK: Cambridge University Press, pp. 5876. doi: 10.1017/CBO9781139794749.006CrossRefGoogle Scholar
Schmid-Hempel, P (2021) Evolutionary Parasitology: The Integrated Study of Infections, Immunology, Ecology, and Genetics. Oxford, UK: Oxford University Press, ISBN: 0198832141.Google Scholar
Sepkowitz, KA (2002) Opportunistic infections in patients with and patients without acquired immunodeficiency syndrome. Clinical Infectious Diseases 34, 10981107.CrossRefGoogle ScholarPubMed
Small, HJ and Pagenkopp, KM (2011) Reservoirs and alternate hosts for pathogens of commercially important crustaceans: a review. Journal of Invertebrate Pathology 106, 153164.CrossRefGoogle ScholarPubMed
Soler, M (ed.) (2018) Avian Brood Parasitism: Behaviour, Ecology, Evolution and Coevolution. Cham, Switzerland: Springer. ISBN: 3319731386.Google Scholar
Stearns, SC (1992) The Evolution of Life Histories. Oxford, UK: Oxford University Press, ISBN: 0198577419.Google Scholar
Szathmáry, E and Maynard Smith, J (1995) The major evolutionary transitions. Nature 374, 227232.CrossRefGoogle ScholarPubMed
Tompkins, DM, Draycott, R and Hudson, P (2002a) Field evidence for apparent competition mediated via the shared parasites of two gamebird species. Ecology Letters 3, 1014.CrossRefGoogle Scholar
Tompkins, DM, Sainsbury, AW, Nettleton, P, Buxton, D and Gurnell, J (2002b) Parapoxvirus causes a deleterious disease in red squirrels associated with UK population declines. Proceedings of the Royal Society B: Biological Sciences 269, 529533.CrossRefGoogle ScholarPubMed
van Dijk, J and De Baets, KD (2021) Biodiversity and host-parasite (co)extinction. In De Baets, K and Huntley, JW (eds), The Evolution and Fossil Record of Parasitism. Cham, Switzerland: Springer Nature, pp. 7597.CrossRefGoogle Scholar
Vihinen, M (2017) How to define pathogenicity, health and disease? Human Mutation 38, 129136.Google ScholarPubMed
Vilcinskas, A (2015) Pathogens as biological weapons of invasive species. PLoS Pathogens 11, e1004714.CrossRefGoogle ScholarPubMed
Wade, M, Wilson, D, Goodnight, C, Taylor, D, Bar-Yam, Y, de Aguiar, MAM, Stacey, B, Werfel, J, Hoelzer, GA, Brodie, ED III, Fields, P, Breden, F, Linksvayer, TA, Fletcher, JA, Richerson, PJ, Bever, JD, Van Dyken, JD and Zee, P (2010) Multilevel and kin selection in a connected world. Nature 463, E8E9.Google Scholar
Yule, KM, Miller, TEX and Rudgers, JA (2013) Costs, benefits, and loss of vertically transmitted symbionts affect host population dynamics. Oikos 122, 15121520.Google Scholar
Zelmer, DA (1998) An evolutionary definition of parasitism. International Journal for Parasitology 28, 531533.CrossRefGoogle ScholarPubMed
Zimmer, C (2000) Parasite Rex: Inside the Bizarre World of Nature's Most Dangerous Creatures. New York City, NY: Free Press, ISBN: 0684856387.Google Scholar
Figure 0

Figure 1. An infection that does not change host lifespan, lifetime reproductive success (LRS) or mean annual fecundity may still increase or decrease the growth rate of host lineages. Representation of 2 hypothetical parthenogenetic host lineages, where individuals' longevity is 3 years, there is no reproduction in the 1st year, and a total of 3 offspring are produced during the 2nd and 3rd years. Above, individuals breed less intensively in the 2nd year and more intensively in the 3rd year, which is reversed below. Shifting the reproduction peak to an earlier period in the life cycle increases growth rate, even though population dynamic indices (longevity, LRS, annual mortality and fecundity rates) are equal. Solid lines represent the survival of individuals to the following year, and dotted lines represent reproduction. Darker circles represent later generations than lighter ones (see also Box 4).