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Reports Ecology, 91(1), 2010, pp. 3–6 Ó 2010 by the Ecological Society of America Parasite virulence, host life history, and the costs and benefits of sex CURTIS M. LIVELY1 Department of Biology, Indiana University, Bloomington, Indiana 47405 USA Abstract. The widespread existence of sexual reproduction is widely considered to be one of the most pressing anomalies for evolutionary theory. One possible solution is that coevolution between hosts and parasites might favor sexual over asexual reproduction (the Red Queen hypothesis), provided infection is genotype specific and highly virulent. This requirement for high virulence has been seen as a limitation of the theory. In the present study, I solve for the cost of sex per reproductive time step of the host, as well as the minimum virulence required to select for sex. The results show that the cost of sex per time step increases with increases in the host’s mortality rate, reaching twofold in annual host species. The results also show that high virulence is not required to select for sexual reproduction, especially in long-lived organisms. These findings might help to explain the paucity of parthenogenesis in organisms having long generation times. Key words: evolution of sex; host; logistic population growth; parasite virulence; Red Queen hypothesis. INTRODUCTION 1980, Lloyd 1980, Hamilton et al. 1990). The intuitive appeal of the hypothesis is that coevolving parasites would seem to be a likely source of selection to provide the kind of rapid response against common host genotypes that would seem necessary to prevent the elimination of sexual populations by asexual clones. On the other hand, based on computer simulations, the theory would seem to require that infections are both common and highly virulent in order to select for obligate sexual reproduction (May and Anderson 1983, Howard and Lively 1994, Otto and Nuismer 2004), which could limit the general applicability of the hypothesis. The simulation models, however, make a number of important assumptions regarding the genetic interface for parasite evasion, the number of parasite exposures per host, and the host’s life history. Generally, in these models, the hosts are assumed to be semelparous annuals. In the present study, I solve analytically for the minimum virulence required for parasite-mediated selection to favor sexual reproduction in iteroparous as well as semelparous hosts. The minimum strength of selection required to prevent the fixation of an asexual clone would clearly depend on the cost of producing males. A previous study suggested that this cost is reduced in species with very high birth rates or very low death rates (Doncaster et al. 2000). The rationale for this suggestion was based on analytical solutions that showed that (1) the carrying capacities of asexual populations is higher than that for Almost 40 years after Maynard Smith asked, ‘‘What use is sex?’’ (Maynard Smith 1971), the persistence of obligate sexual reproduction in the face of competition with obligately asexual clones remains mysterious. The mystery stems from the simple fact that sexual populations produce males, which do not directly produce offspring, leading to a lower per capita birth rate than that expected for asexual populations (the ‘‘cost of males,’’ Maynard Smith 1978). This leads to the expectation that, all else equal, asexual reproduction should dominate. Yet the reverse is true. Sexual reproduction is vastly more common in eukaryotes than asexual reproduction (Bell 1982). Many different ideas have been put forth to explain the long-term persistence of sexual reproduction (Williams 1975, Maynard Smith 1978, Bell 1982, Kondrashov 1993). One idea that has withstood empirical scrutiny, at least in some systems, is the Red Queen Hypothesis (Lively 1987, Busch et al. 2004, Decaestecker et al. 2007, Jokela et al. 2009, King et al. 2009, Wolinska and Spaak 2009). The gist of the Red Queen Hypothesis is that parasites should select against common genotypes, giving an advantage to the production of genetically variable offspring (Jaenike 1978, Hamilton Manuscript received 28 June 2009; revised 28 July 2009; accepted 29 July 2009. Corresponding Editor: L. M. Wolfe. 1 E-mail: [email protected] 3 4 CURTIS M. LIVELY sexual populations, and (2) that the difference in carrying capacities becomes smaller as birth rates increase relative to death rates. I recently found a similar result using a different formulation (Lively 2009). In the present study, I solve for the rate of population growth per reproductive time step for an asexual population immediately following its introduction into a sexual population. This then gives the cost of sex per time step when the asexual clone is rare. This estimate for the cost of sex is then used to determine the minimum virulence required to prevent the fixation of an asexual clone. Ecology, Vol. 91, No. 1 WasexðUÞ Wasexð1Þ Csex 1 . : WasexðUÞ f Csex g Note that the left-hand side of the equation is equal to virulence (V ), as defined above in Eq. 1. Hence selection for sex requires that, at some point during the spread of an asexual clone, V . Vmin ¼ Csex 1 f Csex g V . Vmin ¼ Reports Minimum virulence V¼ WðUÞ WðIÞ : WðUÞ ð1Þ The definition is conceptually identical to that used for inbreeding depression by plant population biologists (Lloyd 1979, Charlesworth and Charlesworth 1987). For sex to be favored, the following must be true, at least at some point before the asexual population eliminates the sexual population: W̄sex . W̄asex ð2Þ where W̄sex is the mean fitness in the sexual population, and W̄asex is the mean fitness in the asexual population. If we let g be the frequency of infection in the sexual population, and f be the frequency of infection in the asexual population, the inequality above becomes where the subscripts I and U refer to infected and uninfected, respectively. Assuming that Wsex(I) is equal to Wasex(I)/Csex, and Wsex(U) is equal to Wasex(U)/Csex, we get gWasexðIÞ þ ð1 gÞWasexðUÞ . f WasexðIÞ þ ð1 f ÞWasexðUÞ Csex ð4Þ where Csex is the cost of sexual reproduction per reproductive time step for the host. If f – (g/Csex) . 0, the result can be rearranged to give the following as the condition for which sex is favored: 1 : 2f g ð7Þ If all the clonal individuals are infected ( f ¼ 1), and none of the sexual individuals are infected (g ¼ 0), the condition reduces to 1 V . Vmin ¼ : 2 ð8Þ Hence, as a limiting case, virulence must be greater than one-half, assuming a twofold cost of sex (Csex ¼ 2). This result is consistent with computer simulations that showed that sexual reproduction would be evolutionarily stable, or that sexuals and asexuals would coexist for V . 1/2 (see Fig. 1 in Howard and Lively 1994). Clearly, the minimum virulence to select for sex would be greater than one half whenever f is less than one, and g is greater than zero. For example, given sterilizing parasites (V ¼ 1), and a twofold cost of sex, the minimum frequency of infection in the asexual population required to select for sexual reproduction must become greater than (1 þ g)/2. Thus if 10% of the sexual population is infected (g ¼ 0.10), then more that 55% of the asexual clone must be infected in order to favor sexual reproduction. On the whole, f would be expected to increase, and g to decrease as the clone becomes common in the population (e.g., Lively 2009). The exact values would be expected to depend on the genetic basis for infection, and the number of exposures to parasite propagules. The cost of males revisited gWsexðIÞ þ ð1 gÞWsexðUÞ . f WasexðIÞ þ ð1 f ÞWasexðUÞ ð3Þ ð6Þ where Vmin is the minimum virulence required to select for sex. Thus, for a twofold cost of sex (Csex ¼ 2), the condition becomes MODELS Virulence is normally defined in the theoretical literature as the increase in host death rate caused by infection (e.g., Anderson and May 1982, Levin 1996). One difficulty with this definition is that it does not consider the effects of infection on total host fitness as mediated through fecundity. Here I use a different definition that allows for infection-mediated reductions in fecundity and/or survival. Specifically, virulence (V ) is defined as the difference between the fitness of uninfected, W(U), and infected individuals, W(I), divided by the fitness of uninfected individuals (Lively 2006): ð5Þ An asexual lineage will increase when rare when Csex ¼ Atþ1 1 ½D þ yð1 DÞ þ Bð1 xÞ ¼ .1 Stþ1 1 D þ ð1 sÞB ð9Þ where the numerator (Atþ1) gives the per capita growth rate for an asexual clone per reproductive time step; and the denominator (Stþ1) gives the per capita growth rate for a sexual population per reproductive time step. The variable B is the birth rate for both sexual and asexual females, and D is the death rate, which is constrained to be greater than zero, and less than or equal to one (0 , D 1). The variable s is the frequency of males in the sexual population; x is the birth-rate cost of asexual January 2010 PARASITE VIRULENCE AND THE COST OF SEX reproduction; and y(1 – D) gives the increase in the death rate in the asexual population. The birth and/or death rates would be expected to be functions of total host density. At carrying capacity for the sexual population, the death rate (D) is equal to the per capita birth rate [(1 – s)B]; hence: B ¼ D/(1 – s). Substituting for B in Eq. 9, the condition for the spread of an asexual clone into a sexual population at carrying capacity is given by yð1 DÞ : ð10Þ ð1 xÞ .ð1 sÞ 1 þ D Csex ¼ 1 þ D: ð11Þ Hence, the cost of sex per time step increases linearly with increases in D, reaching twofold in annual populations (D ¼ 1). Note that there is no cost of sex per time step when Csex is equal to one, which is the case for an immortal sexual population (D ¼ 0). Eq. 11 gives the cost of sex per reproductive time step. What about the cost of sex per generation? The intrinsic advantage of asexual reproduction per host 1=D generation is simply Csex ¼ (1 þ D)1/D, where 1/D gives the average number of time steps per generation (assuming the birth and death rates are constants). Thus, taking the limit, the intrinsic advantage of asexual reproduction per generation converges on the exponential (2.72) as the death rate approaches zero. Thus the cost of sex per generation may be greater than 2, owing to the ‘‘compound interest’’ accrued from offspring produced in the early time steps. The cost of sex per generation decreases to twofold in an annual population (D ¼ 1). Assuming that parasites can infect during each time step for the host, the relevant cost of sex may be the expected cost per time step, rather than the cost per generation. If parasites are virulent enough to counter the cost of sex per time step, they could prevent the short-term fixation of asexual clones. Substituting the result for the cost of sex per time step (Eq. 11) into Eq. 6, the minimum virulence required to select for sex becomes the following: D : f ð1 þ DÞ g ð12Þ For f ¼ 1 and g ¼ 0, the equality simplifies to Vmin ¼ D : 1þD ð13Þ Thus, the limiting case for virulence becomes V . 1/2 only if the death rate is equal to unity (D ¼ 1). For lower values of D, the condition becomes less stringent. For example for D ¼ 1/2, the limiting case becomes V . 1/3. As such, the maintenance of sex in long-lived species may be less problematical. DISCUSSION The results show that the cost of producing males depends on the death rate in the sexual population. In the extreme, there is no cost of sex per time step in immortal sexual populations. The cost of sex per time step increases linearly to twofold when the death rate is equal to one, as in annual populations. The minimum virulence to select for sexual reproduction, therefore, deceases with increases in the death rate. The minimum virulence to select for sex is also reduced as (1) the fraction of infected asexual individuals increases, and/or (2) the fraction of infected sexual individuals decreases, both of which happen rapidly in simulation models as the clone becomes common (Lively 2009). Doncaster et al. (2000) were the first to suggest that the cost of sex might be affected by the birth and death rates in the sexual population. They showed that the carrying capacities of asexual populations can be higher than that of sexual populations, and that this difference decreases as the intrinsic birth rate increases relative to the death rate (see also Lomnicki 2001, Olofsson and Lundberg 2007). Based on this result, Doncaster et al. (2000) suggested that ‘‘males are less costly to species with high growth capacities.’’ In the present paper, I solved for the cost of sex at carrying capacity for the sexual population. Here the cost of sex does not depend on the intrinsic birth or death rates per se, but rather on the equilibrium values, which vary from zero to one. The results nonetheless suggest that Doncaster et al. (2000) were correct in suggesting that the cost of sex depends on the life histories of the sexual and asexual populations. Reducing the cost of sex reduces the strength of selection required to maintain it. Previous studies have focused on resource competition between sexual and asexual populations, and have suggested that coexistence is easier in long-lived species (Doncaster et al. 2000, Olofsson and Lundberg 2007, Scheu and Drossel 2007). The results of the present study similarly suggest that the minimum parasite virulence required to prevent the fixation of an asexual clone decreases with the host’s death rate. Thus it may be that highly virulent parasites are only required for the evolutionary persistence of sex in short-lived host species. If so, these results may help Reports Hence the condition for the spread of the asexual population depends strongly on the death rate. If, for example, the death rate is one, as in an annual population, then the condition for spread of the clone is (1 – x) . (1 – s). As the death rate approaches zero, the condition becomes y , 0, suggesting that a clone would not spread into an immortal sexual population. The intrinsic advantage of asexual reproduction, in the absence of any costs (x ¼ y ¼ 0), can be solved for by substituting 0 for x and y in equation (9). At carrying capacity for the sexual population [B ¼ D/(1 – s)], and assuming an equal sex ratio (s ¼ 1/2), the advantage of asexual reproduction per reproductive time step is simply Vmin ¼ 5 6 CURTIS M. LIVELY to explain the paucity of obligate asexual reproduction in large organisms having long generation times (Bell 1982). CONCLUSIONS Decreasing the death rate of uninfected individuals has two effects that are favorable to the Red Queen hypothesis. First, it decreases the cost of sex per time step, thereby reducing the minimum virulence to favor sex. Second, it reduces the rate of spread of a clone into a sexual population, which increases the time (in generations) for parasites to respond to the clone before it goes to fixation. Taken together, these factors suggest that asexual reproduction should be more common in annuals, and that sexual reproduction should be more common in long-lived iteroparous species. Sex might also be expected to be more common in stable, resourcelimited populations. ACKNOWLEDGMENTS Reports I thank Aneil Agrawal, Lynda Delph, Hadas Hawlena, Jukka Jokela, Kayla King, Maurine Neiman, and anonymous reviewers for helpful suggestions. This study was supported by the U.S. National Science Foundation (DEB-0515832, DEB0640639). LITERATURE CITED Anderson, R. M., and R. M. May. 1982. Coevolution of hosts and parasites. Parasitology 85:411–426. Bell, G. 1982. The masterpiece of nature: the evolution and genetics of sexuality. University of California Press, Berkeley, California, USA. Busch, J. W., M. Neiman, and J. M. Koslow. 2004. Evidence for the maintenance of sex by pathogens in plants. Evolution 58:2584–2590. Charlesworth, D., and B. Charlesworth. 1987. Inbreeding depression and its evolutionary consequences. Annual Review of Ecology and Systematics 18:237–268. Decaestecker, E., S. Gaba, J. A. M. Raeymaekers, R. Stoks, L. Van Kerckhoven, D. Ebert, and L. De Meester. 2007. Host– parasite ‘‘Red Queen’’ dynamics archived in pond sediment. Nature 450:870–873. Doncaster, C. P., G. E. Pound, and S. J. Cox. 2000. The ecological cost of sex. Nature 404:281–285. Hamilton, W. D. 1980. Sex versus non-sex versus parasite. Oikos 35:282–290. Hamilton, W. D., R. Axelrod, and R. Tanese. 1990. Sexual reproduction as an adaptation to resist parasites: a review. Ecology, Vol. 91, No. 1 Proceedings of the National Academy of Sciences (USA) 87: 3566–3573. Howard, R. S., and C. M. Lively. 1994. Parasitism, mutation accumulation and the maintenance of sex. Nature 367:554– 557. Jaenike, J. 1978. An hypothesis to account for the maintenance of sex within populations. Evolutionary Theory 3:191–194. Jokela, J., M. Dybdahl, and C. M. Lively. 2009. The maintenance of sex, clonal dynamics, and host–parasite coevolution in a mixed population of sexual and asexual snails. American Naturalist 174:S43–S53. King, K. C., L. F. Delph, J. Jokela, and C. M. Lively. 2009. The geographic mosaic of sex and the Red Queen. Current Biology 19:1438–1441. Kondrashov, A. S. 1993. Classification of hypotheses on the advantage of amphimixis. Journal of Heredity 84:372–387. Levin, B. R. 1996. The evolution and maintenance of virulence in microparasites. Emerging Infectious Diseases 2:93–102. Lively, C. M. 1987. Evidence from a New Zealand snail for the maintenance of sex by parasitism. Nature 328:519–521. Lively, C. M. 2006. The ecology of virulence. Ecology Letters 9: 1089–1095. Lively, C. M. 2009. The maintenance of sex: host–parasite coevolution with density-dependent virulence. Journal of Evolutionary Biology 22:2086–2093. Lloyd, D. G. 1979. Some reproductive factors affecting the selection of self-fertilization in plants. American Naturalist 111:67–79. Lloyd, D. G. 1980. Benefits and handicaps of sexual reproduction. Evolutionary Biology 13:69–111. Lomnicki, A. 2001. Carrying capacity, competition and maintenance of sexuality. Evolutionary Ecology Research 3. May, R. M., and R. M. Anderson. 1983. Epidemiology and genetics in the coevolution of parasites and hosts. Proceedings of the Royal B 219:281–313. Maynard Smith, J. 1971. What use is sex? Journal of Theoretical Biology 30:319–335. Maynard Smith, J. 1978. The evolution of sex. Cambridge University Press, Cambridge, UK. Olofsson, H., and P. Lundberg. 2007. The twofold cost of sex unfolded. Evolutionary Ecology Research 9:1119–1129. Otto, S. P., and S. L. Nuismer. 2004. Species interactions and the evolution of sex. Science 304:1018–1020. Scheu, S., and B. Drossel. 2007. Sexual reproduction prevails in a world of structured resources in short supply. Proceedings of the Royal Society B 274:1225–1231. Williams, G. C. 1975. Sex and evolution. Princeton University Press, Princeton, New Jersey, USA. Wolinska, J., and P. Spaak. 2009. The cost of being common: evidence from natural Daphnia populations. Evolution 63: 1893–1901.