Abstract
In isolated populations underdominance leads to bistable evolutionary dynamics: below a certain mutant allele frequency the wildtype succeeds. Above this point, the potentially underdominant mutant allele fixes. In subdivided populations with gene flow there can be stable states with coexistence of wildtypes and mutants: polymorphism can be maintained because of a migration-selection equilibrium, i.e., selection against rare recent immigrant alleles that tend to be heterozygous. We focus on the stochastic evolutionary dynamics of systems where demographic fluctuations in the coupled populations are the main source of internal noise. We discuss the influence of fitness, migration rate, and the relative sizes of two interacting populations on the mean extinction times of a group of potentially underdominant mutant alleles. We classify realistic initial conditions according to their impact on the stochastic extinction process. Even in small populations, where demographic fluctuations are large, stability properties predicted from deterministic dynamics show remarkable robustness. Fixation of the mutant allele becomes unlikely but the time to its extinction can be long.
Author Summary
Underdominance is a component of natural evolution: homozygotes – of either wildtypes or mutants – are advantageous. This can play a role in speciation and as a method to establish artificial genetic constructs in wild populations. The polymorphic state of wildtype and mutant alleles is unstable. However, in subdivided populations limited gene flow can counterbalance this effect. The maintenance of polymorphism sensitively depends on the amount of gene flow. In populations of finite size, the polymorphism is ultimately lost due to stochastic fluctuations, but there are long intermediate periods of polymorphism persistence. We analyze a simple population genetic model to characterize and explore the polymorphic phases depending on population size and genotypic fitness values. Even for large fluctuations (small population size), long periods of neither extinction nor fixation are possible. Since underdominance has been proposed as a genetic strategy in the pest management of disease vectors, it is important to understand the basic features of this system precisely, especially with a focus on gene flow between ecological patches. We assess different release strategies of potentially underdominant mutants, where one seeks to minimize the probability of fixation of the introduced allele but maximize the time to its extinction.
Introduction
A population can evolve due to differences in relative reproductive success over a life cycle. Fitness, in an evolutionary genetic sense, is defined as the relative expected number of descendants in the next generation based on an individual's genotype. In diploid organisms, two alleles can result in three genotype combinations, two homozygous genotypes with two copies of the same allele, and one heterozygote type with one copy of each allelic type. Heterozygote disadvantage in reproductive success is termed underdominance: Heterozygous individuals have a lower relative fitness than both homozygotes. The fundamental properties of underdominance in large populations with deterministic dynamics are well known [1], [2], [3]. Underdominance acts as an evolutionarily bi-stable switch. A mutant allele that is in underdominance with the wildtype is expected to be lost if its initial frequency is below a certain threshold. However, if the initial frequency is above this threshold frequency, it can also proceed to fixation. The threshold frequency is determined by the fitness values of the genotypes involved [4], [5]. The evolutionary dynamics induced by underdominance are similar to those in a coordination game, such as the stag hunt [6], [7], [8], [9], [10].
Under natural conditions underdominance can be caused by chromosomal rearrangements [11]. These rearrangements can accumulate between closely related species [12], [13], despite an exceedingly small predicted probability of becoming established [14], [15]. Individuals that are heterozygotes for a reciprocal translocation suffer from reduced fertility compared to homozygotes. This is due to a disrupted number of gene copies in the affected chromosomal region (i.e. segmental aneuploidy) [16].
We focus on the dynamics of a single locus with underdominant alleles of large fitness effects, such as those expected with natural reciprocal translocations. There has also been research into multiple loci of weaker individual effects, which can have interesting self-organizing properties [17], [18]. Alternatively, ‘engineered underdominance’ approaches based on reciprocal suppression of toxic constructs have also been proposed, which have much lower thresholds for a population transformation than typically expected [19], [20]. Finally, frequency dependent interactions can have underdominant-like properties, such as maternal-effect chiral dynamics in snails [21], and the Rh factor in humans [22]. However, details of these additional cases are beyond the scope of the work described here. Our results apply to classical single locus underdominance with large fitness effects.
As an artificial genetic construct, underdominance has been proposed as a method to stably establish linked alleles with desirable properties in the wild; for example, rendering insect populations resistant to diseases that otherwise can be transferred to humans (or other species), such as malaria or Dengue fever [23]. The bi-stable nature of the evolutionary dynamics suggests that a sufficient release of transformed individuals will ultimately result in complete fixation of the transformed allele in the population. Additionally, the system is reversible: A release of a sufficient number of wildtypes can bring the population back to its original state.
Underdominant polymorphism is eventually lost or completely fixed in single populations. However, it is known that it can become stable at mixed frequencies due to a migration-selection equilibrium in large subdivided populations that exchange a fraction of migrants [24], [25], [26]. An underdominant polymorphism can be maintained if the migration rate is below a bifurcation point, which depends on the genotypic fitness values [26]. Higher migration rates result in sufficient mixing, such that the two population system effectively reduces to a single population and the polymorphic state is lost.
Initial testing of genetic pest management systems is likely to take place on more isolated physical or ecological islands [27], [28], [29]. Furthermore, there are potential conservation applications of this type of technology in many island species [30]. However, smaller insect population sizes on islands may not be well approximated by deterministic dynamics based on an infinite population assumption. Here, we extend the understanding of the evolutionary dynamics of underdominance in two demes to include stochastic effects in finite populations.
Generations are overlapping in species that do not strictly follow discrete time reproductive patterns. Hence, we concentrate on Moran models describing the stochastic invasion and fixation of transformed or mutant alleles in a system of coupled populations. A Moran process considers a single reproductive event in one time step such that after time steps in a population of fixed size , each individual has reproduced once on average. If the timescales are small enough that further mutations can be excluded, loss or fixation of a given allele are the only possible outcomes. As a simplification to our stochastic model, we assume that the two populations exchange migrants at the same rate. How likely are extinction or fixation of a certain number (release) of genetically transformed mutant alleles? A release strategy can be defined by number of released individuals and the release fractions in each sub-population. How long can we expect a successfully transformed local population to maintain the modified allele? How robust is the notion of stability from the deterministic system in the presence of fluctuations? We are also interested in population size asymmetry, where a simplified island-continent model can be appropriate.
The manuscript is organized in the following way. The next part of this section briefly repeats aspects of evolutionary dynamics in two infinitely large populations coupled by migration. Then, we introduce our model based on a Moran process for two populations with migration. The section ends with the introduction of a one-dimensional island continent model, which directly follows as a solvable limit case. In the Models section we first give the precise formulation of the discrete stochastic dynamics in two dimensions and argue how to access its properties by simulations. Secondly, we derive the island-continent model, which allows a prediction for the mean extinction times of the mutant allele in a small island population. In the last section, all results are discussed, followed by a concluding summary.
Replicator dynamics
With we denote the wildtype allele, whereas represents a transformed (or mutant) allele. Given a single locus two allele model of diploid organisms, there are three genotypes possible: , , and . We set the average allelic fitness of wildtypes () to , the fitness of heterozygote genotype () to , and the fitness of homozygous mutants () to . The fitness ordering leads to underdominance. Under random mating, we can describe the population by the frequencies of the alleles (i.e., random union of gametes predicts the relative abundance of initial zygotic genotypes in the population before applying selection). For allele with relative abundance in a single population, the average fitness is then given by . Likewise, for the wildtype allele we have . In general, for overlapping generations, a replicator equation describes the change in allele frequency in an infinitely large (well mixed) population in continuous time,
(1) |
Here, denotes the temporal derivative and is the average fitness of the population. The roots of Eq. 1 give the fixed points . In the case of underdominance, , we have the stable fixed points and as well as the unstable fixed point .
For two local populations that exchange migrants we introduce the rate of migration as a macroscopic parameter. In a small time interval , the fraction of immigrants is . Hence, is the fraction of non-migrant individuals. Let be the frequency of allele in population . With the flow of alleles from the other population due to migration, the frequencies that contribute to the change in over time are , where , in both populations. The total average fitness in either population is . Hence, the replicator equation for the coupled system () reads
(2) |
These dynamic equations follow from Eq. 1, [26]. The number of fixed points and their stability properties depend on the rate of migration. The points and are always stable. Migration has no effect on the diagonal . Exchanging alleles between populations at equal frequencies results in no change in either of them. The point on the diagonal is an unstable fixed point, reflecting the inner unstable point of the single population case. For symmetric underdominance, , and , there are two stable states in the interior of the joined allele frequency space, i.e. where is neither fixed, nor lost. These stable fixed points of the dynamics are located on the symmetry axis, . For general fitness values , this symmetry is broken, but such internal stable equilibria can still exist below a critical migration rate [26].
Moran process
We focus on a Moran model with fixed population sizes. Our main assumption is that mate choice is random. In this case individuals in the population can be thought of as passing through the Hardy-Weinberg expectations at some point in life-cycle before selection. Hence, we can consider the system as if individual alleles (i.e. gametes) reproduce and die. Reproduction is proportional to fitness and death is random. Such discrete stochastic birth-death processes are typically used to describe the (transient) microscopic evolutionary dynamics in single uncoupled populations of finite size [31], [32], [33], [34], [35], [36]. From the microscopic dynamics, one is interested in macroscopic quantities such as the probability of extinction, and the associated extinction times.
Our two populations are of size and . The number of individual copies of the mutant allele (type ) in each population are and , jointly defining the state. Thus, type has frequencies , , respectively. As we are concerned with diploid organisms the total number of alleles in each population is , where is the number of organisms in population . Time is scaled in units of half the time between organismal reproduction events, i.e. the time between individual allele reproduction events. For convenience we introduce the fractions and . The average allelic fitness functions are
(3) |
(4) |
For a consistent stochastic model several events have to be considered independently in one time step of the Moran process.
First, with probability a reproductive event occurs in population . With probability a reproductive event occurs in population . We exclude simultaneous reproductive events in both populations and treat the two population system as one Markov chain with the two absorbing states , and . One population may change more rapidly than the other (i.e. more events occur in the larger population per unit time). If is the relative reproductive rate under neutrality (), we have , and thus . Hence, for the study of two populations of comparable size, it is convenient to set . The choice of does not change the migration-selection equilibria predicted by the replicator system Eq. 2, compare Fig. 1. Only the rates of change between fixed points are increased in larger populations.
Secondly, in population , the number of alleles of either type increases with a probability proportional to the average fitness of the allele. In such an event, however, we have to consider that with probability , the parent individual allele is from the other population (i.e., an immigrant). Hence, type produces an identical offspring with probability proportional to . A similar probability holds for type offspring, .
Thirdly, in each population, the total number of alleles is held constant. This implies that for each birth event, there is an independent death event: a randomly chosen individual allele is removed from the population. A type allele is removed with probability , a type allele is removed with probability .
Overall, given the state , there are five events possible. Four of them involve a change in allele frequency , or . Hence, we have to define four transition probabilities in each state, , such that migration and selection only contribute to birth and not to random death. In general, fixation or loss in both populations are the only absorbing states, i.e. . Due to migration, there is a non-vanishing flow perpendicular to the boundaries in state space. When the mutant allele is lost or fixed in only one population, immigrants can drive the system back into the interior, where is present in both populations, compare Fig. 1 and Fig. 2.
Limiting cases
Let us first consider an island and continent situation. On the large continent, migrants from the small island introduce at a very low frequency. The wildtype allele is fixed and allele cannot invade by migration. However, there is a non-vanishing fitness contribution due to migration to the island, which receives wildtype immigrants from, and loses migrants of any type to the continent. This can be described by the limit case of the two population system where one population becomes infinite and the other remains finite. Given the fitness functions Eqs. 3 and 4, an equivalent limit case is . Applying this limit to the transition rates , the single stochastic variable becomes , and time can be rescaled such that drops out. This yields a one-dimensional birth-death process on . The one-dimensional transition probabilities are and . Here, , (), where , and . The continent can only contribute to the birth of wildtype homozygotes. Thus, , and .
In the Models section we show how the moments of the extinction times associated with the extinction process on the island starting with mutant alleles can be determined. The probability that allele ultimately vanishes in the island population is . For , the moment follows recursively from
(5) |
Of most interest is typically the mean life time, or mean extinction time, of the allele , .
Another case that leads to one-dimensional evolutionary dynamics is the limit of high migration rate, such that the two populations become genetically indistinguishable. This yields slightly different dynamics in a population of individuals, namely a one-dimensional Markov chain with two absorbing boundaries. For such processes the extinction/fixation times are formally well understood [31], [37]. The expression for the mean extinction time of a mutant allele at frequency is similar to Eq. 5 with , [33].
Models
Moran process for two coupled populations
With migration the number of alleles in each population is , and . Here, , and . The transition probabilities are given by
(6) |
(7) |
(8) |
(9) |
where , and the equivalent , are the average fitness values in each population. The probability that the state does not change (e.g. when a type dies and another type is born) is thus given by . The only trivial boundary conditions are , and for . To assess the dynamics of the system, we directly simulate the stochastic process described by Eqs. 6–9.
Lifetime in an island population close to a continent
The average allelic fitness values in the island population of size are
(10) |
(11) |
Note here that for the rescaled allele frequency , we just have , as well as , compare Eqs. 3 and 4. The transition probabilities of the one-dimensional Moran process are
(12) |
(13) |
where the normalization (total fitness) is given by .
The parameter transition from high to low migration leads to a change of the local gradient of selection , Eqs. 12 and 13. The boundary is absorbing, while is reflecting,
(14) |
Note that does not depend on the size of the island population. Furthermore, has the trivial solution , and can have two non-trivial solutions , given by
(15) |
which is real valued if . Hence for
(16) |
the deterministic one-dimensional dynamics has a stable fixed point at , and an unstable one at .
Let be the probability that the process moves from state to state in exactly time steps. For this probability function the backward master equation
(17) |
holds, for which we can compute the conditional moments in the following way. The only absorbing state is , as is reflecting, , for . We call the moment of the life time of the process starting from any . For these moments, the following moment generating recursions hold [31], [33], [38]:
(18) |
where for the zeroth moment we have , which is the probability that the system fixes at after an arbitrary number of (but at least ) steps. Hence, for the mean life time, , i.e. the first moment of the process, we find
(19) |
which we can solve recursively. Introducing , we get
(20) |
which, respecting the boundary condition and starting from , solves to
(21) |
Changing to (and the upper limits of sum and product accordingly), we see that , such that the mean life time, starting from any , fulfills
(22) |
Similarly, all moments follow from Eq. 18, leading to Eq. 5 [33].
Results/Discussion
Extinction events in two populations of comparable size
First, we address the ratio of fixation to loss in the system of two coupled sub-populations of equal size. An ideal case for a locally controlled genetic pest management strategy emerges when the resistant allele () is at high frequency in one local population and at very low frequency in another. Given the situation of almost-all in one population, and almost-no in the other, what is the probability of the allele to become extinct in both populations, , relative to the probability to reach (typically undesired) complete fixation, ? The answer is given in Fig. 3 (a) showing the ratio , for 40 alleles in each population, as a function of increasing fitness asymmetry , with heterozygote fitness kept constant . The ratio of fixation to loss of approaches zero with decreasing fitness of homozygote mutants . The rate of decay decreases with increasing migration rate, as for low values of the system spends long times in the interior, compare to the histogram in Fig. 4. In addition, the frequency distribution becomes broader with increasing , see Fig. 3 (b).
The replicator dynamics for two populations shows a maximum of nine fixed points and an associated bifurcation pattern depending on the migration rates, see Fig. 1 and compare to [26]. A stable interior equilibrium at migration-selection balance can be disturbed by the demographic fluctuations and will ultimately result in fixation or loss of one of the alleles, despite the stability of the original situation. Hence, one is interested in the average extinction time under various parameter configurations. To grasp an idea of how the system behaves in a single realization, we show three typical stochastic trajectories, Fig. 2. Naively, one would expect the system to spend more time near interior stable equilibria. However, the process spends most of its time in the adjacent edges and corners of the joint allele frequency space, where waiting times are long. The system exits the regions around stable points (e.g., near the corner) via the edge rather than on internal trajectories, see Fig. 2, because the demographic noise is proportional to [31]. Hence, in the non-absorbing corners there is little noise and thus we expect long waiting times. Between corners and especially in the interior away from the edges the dynamics are relatively fast. An example histogram of extinction events is given in Fig. 4 (a). For instance, the mean extinction time in a system with alleles is time steps for small . The extinction process spends most of its time near the or corner. For a very long time the mutant allele is essentially fixed in one population and lost in the other. However, if migration rates become larger, the length of this quasi-stable period decreases ( for ), compare to Fig. 5.
The impact of system size in two equally large populations can now be quantified in terms of the average extinction time of type . The extinction time diverges with increasing population size. Fig. 4 indicates that for lower migration rates, this effect is stronger. Low migration, , gives an average extinction time of approximately 30000 time steps, which amounts to approximately 375 generations in a populations of 80 alleles. For high migration, , we obtain an average of approximately 2500 time steps (approximately 31 generations). This number of generations is consistent with the expectation that the two populations become panmictic for high migration: In a panmictic population of 160 alleles, the standard literature on Moran models [33], [39] yields an average extinction time of approximately 2500 time steps (approximately 16 generations).
Analyzing the extinction times as a function of migration rate reveals the transition from one power law to another in the region around the critical migration rate predicted by the replicator system; We can identify two regimes. In the first regime, , the extinction time scales as , with . In the second regime, , the extinction time scales as , with . The two power law regimes for are given in Fig. 5 for a realistic choice of genotypic fitness values and . For this parameter configuration the replicator equation 2 yields a critical value of [26]. Fig. 5 analyzes this transition for . The initial condition is chosen such that are at or close to the selection-migration equilibria, , which is near the most efficient release strategy in terms of minimal release numbers (discussed below).
Temporary maintenance of polymorphism in an island population
The transition of one population approaching infinite size, while the other remains relatively small, leads to stochastic evolutionary dynamics in one dimension. A benefit in using a Moran model is that in one dimensional systems we can obtain exact analytical results for the hierarchy of moments of extinction/fixation times [31], [33], [38], [39]: We can solve the recursions for the moments, Eq. 18. In Fig. 6 we present the convergence of the limit , (, ) and show histograms from simulations of the one-dimensional island model, Eqs. 12 and 13. The distribution of extinction times changes substantially with . In our example, for very low migration rates the mutant allele is expected to be maintained in the system for more than generations, when starting from . With a fixed population ratio, we average over the change of the Moran process in the island population to obtain a measure , discarding changes in the continent population. As the ratio increases, this average converges to the average extinction time : The simulations start from , , and with increasing , fluctuations in the continent population decrease, . Only for a continent population which is roughly a hundred times larger than the island population, we enter the regime of a quasi one-dimensional system with a static continent of wildtypes. The limit case is not approached monotonically, but depends on the migration rate in a non-trivial way.
Release strategies and probability of long term transformation
Assuming migration is low enough such that it can be locally counteracted by selection, how likely is a mutant allele to fix or be removed depending on the initial transformation? Here, we give a characterization of the two population system in terms of complete loss or fixation in both, or temporary reciprocal fixation and loss. In principle, a release strategy is based on two parameters. First, the amount of new mutant alleles added to the system, , relative to the size of each population. Second, a fraction is released into one, and the remainder into the other population. Maintaining the populations at a constant size implies that
(23) |
is the set of initial release points, where ranges from to . For a given , this defines a curve in the joint allele frequency space, which is depicted in Fig. 7 for different values of . Also in Fig. 7 the probabilities of first visiting a corner of the system for a fixed release size and various fractions are summarized as a function of the population sizes . In accordance with Fig. 3, the system loses the mutant allele entirely with a high probability for a wide range of chosen release strategies.
Fig. 7 illustrates some less intuitive properties that are informative in terms of release strategies. For a given number of genetically modified individuals , it might seem that releasing all of the individuals into a single target population would maximize the chance of successfully transforming the population. However, in this case, simultaneously releasing some individuals into the neighboring population is more likely to result in a successful local transformation. This proportion is dependent on the population size, for to for or higher. To understand this dependency, note that the basin of attraction of the local transformation is a smaller proportion of the local space near the central unstable equilibrium. Since the demographic noise in finite populations is proportional to , the basin of interest comprises a smaller proportion of states where selection can be counterbalanced by local migration. In the illustrative example in Fig. 7 it can also be seen that a simultaneous equal release into both populations () maximizes the chances of transforming both. Attempting to transform one population at a time in a stepwise strategy does not lead to complete fixation immediately. However, once a single population is successfully transformed, it is much easier to transform the neighboring population, if desired. This only requires an additional release of less than a single population size, .
Summary and conclusions
We have proposed a simple model to analyze the influence of small system size and system size asymmetry on the evolutionary dynamics of an underdominant system in a structured population. The population structure itself is chosen to be as simple as possible: We consider two sub-populations that exchange migrants at a given rate. This allows a direct comparison with findings in infinitely large populations [24], [26]. Our simplifying assumptions then permit a statistical characterization of the migration-selection equilibrium in finite populations by means of simulations. Other stochastic descriptions of the evolutionary dynamics, e.g., the Wright-Fisher process, have very similar properties when it comes to extinction probabilities and times [31], [40], [41]. However, we stick to a Moran model which has the benefit that limit cases have exact solutions for all fitness values and population sizes that do not rely on further approximations.
We review previous findings in infinitely large populations in the introduction and use them as a basis to examine the influence of demographic fluctuations in small populations. We argue that the transient dynamics are important, as the influence of noise may alter the outcome of the evolutionary dynamics in this regime.
Our main results can be summarized as follows. First, for fitness asymmetry, extinction rather than total fixation of the potentially underdominant allele is the most likely outcome, even if this allele is initially at high frequency in one of the populations. In a migration-selection equilibrium the (quasi-stationary) variance in allele frequencies is low. High migration disrupts this dynamic equilibrium such that extinction is facilitated and the variance in frequency increases.
Second, we find that migration rate has a strong impact on the extinction process. We identify a threshold below which the mutant allele can be maintained for a long time, which corresponds to a bifurcation point in the deterministic system. For example, if mutant homozygotes suffer from a fitness loss and heterozygotes from a fitness loss (compared to wildtypes), extinction is significantly delayed for migration values below . With increasing population sizes, the extinction times tend to diverge rapidly with decreasing migration in this regime. Even in small populations, disruptive effects from demographic fluctuations can be counterbalanced by small, but finite numbers of migrants.
Third, we evaluate the consequences for release strategies. For conservative estimates of a release of potentially underdominant mutants into wildtype populations, we can give a statistical evaluation that can be tested in vivo, as well as in situ. If migration between patches is low enough, a release division of mutants into a target population, and thus into a neighboring population, can be optimal and lead to a local polymorphism that is expected to be maintained for a long time.
Fourth, the limit case of one population becoming very large reveals that the potentially underdominant allele can be kept in the small population for long times. A small population with incoming migrants from a large wildtype reservoir is well described by a one-dimensional process if the reservoir is about times larger. This also refers to the desired situation in which one is interested in the local establishment of disease resistance (caused by an effector gene), driven by underdominance.
Results from infinite population assumptions may, in some cases, be misleading when observing finite allele frequencies. Under demographic fluctuations the stochastic evolutionary dynamics slow down near corners and along edges: In the vicinity of equilibrium points the flow induced by selection can become squeezed between boundary and equilibrium. High flow density means low flow velocity, which also affects the transition rates. Due to this nature we may observe large waiting times near the corners and along edges which happen to be near internal equilibria. However, under neutral evolution, the system also slows down near corners and edges.
If selection is strong, underdominance and sufficiently low migration can maintain a polymorphic state for many generations even in small populations. This bodes well for using underdominance to control initial testing of genetically modified insects in isolated settings so that the natural species remains untransformed in its broader range. The system can be stable for so long that additional factors are likely to be more important in ultimately disrupting the system. Such additional factors can be the occurrence of new mutations and/or behavioral changes [42], [43], [44].
The stability properties of underdominance in small finite populations may have particular value both in initial testing of genetically modified vectors and in species conservation applications. For example, Culex quinquefasciatus mosquitoes have spread from a native range in the southeastern United States to several islands in the Pacific due to human activities. Most of these islands are of substantial conservation value, e.g., the Galápagos [45] and Hawaiian archipelagoes [30]. The mosquitoes are vectors of avian malaria, Plasmodium relictum, which is a major factor in past extinctions and current endangerment of many Hawaiian forest birds [30]. Island populations of C. quinquefasciatus can be genetically modified to be refractory to avian malaria to break the cycle of infection, e.g., [46], [47]. Linking this refractoriness to underdominance could prevent the genetic modifications from spreading back into the native range of C. quinquefasciatus. This would allow the native range mosquitoes to be protected in a wildtype state. Furthermore, it may also be possible to leave a fraction of the island populations stably untransformed to allow the evolution of natural resistance in the threatened bird species (see, e.g., [48]).
Genetically modified chromosomes are typically less fit than wildtypes as homozygotes, see [49] and references therein. This homozygote fitness asymmetry provides a degree of failsafe into the system. If stability is lost, the system is much more likely to result in a return to a natural wildtype state, rather than reaching fixation of an artificial genetic modification across populations.
Acknowledgments
P.M.A acknowledges discussions with Maria Abou Chakra.
Footnotes
The authors have declared that no competing interests exist.
PMA and AT acknowledge financial support from the Deutsche Forschungsgemeinschaft and the Max-Planck-Society. FAR acknowledges support by funds from the University of Hawai'i at Manoa, the Deutsche Forschungsgemeinschaft RE-3062/2-1, and funds from the Max Planck Society. All funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
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