# Landmarking and strong Allee thresholds

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## Abstract

Mate-finding difficulties in small populations are often postulated to create strong demographic Allee effects that increase the probability of extinction of native species or, similarly, decrease the probability that non-native species will successfully invade. Many species make use of a restricted number of mating locations, detectable from long-distance, that are not selected for habitat reasons (e.g., hilltopping in butterflies). This ‘landmarking’ strategy may specifically address the problem of overcoming mate-finding difficulties. Using a variant of the birthday problem, we demonstrate that populations which locate a restricted number of mate-finding sites using landmark features may have high probability of successful mating even at very low population densities. Therefore, a strong Allee threshold, if it exists, may be very small, and non-native species that make use of this strategy may have a very good chance of population establishment at low density.

## Keywords

Hilltopping Birthday problem Endangered species Invasive species Mate encounter Establishment Population growth rate## Introduction

When the number of non-native individuals introduced to a region is small, a demographic Allee effect may act to reduce invasion success (e.g., Drake and Lodge 2006). The existence of a strong Allee effect, where there is a threshold population density below which population growth is negative (e.g., Deredec and Courchamp 2007), may doom small populations to extinction. Mate-finding difficulties have been identified as the most common component of Allee effect that causes a strong demographic Allee effect (Gascoigne et al. 2009; Kramer et al. 2009). Moreover, it has been predicted that difficulty in mate-finding at low densities can be a major stumbling block for the establishment success of non-native species (Veit and Lewis 1996; Taylor and Hastings 2005; Deredec and Courchamp 2007; Kramer et al. 2008).

While we are accustomed to thinking about mate-finding difficulties as potential controls on the success of invasive species, some mechanisms can lead to success even at a very low density of newly introduced individuals. We examine the impact of one little-studied mechanism of mate-finding, landmarking, on strong Allee thresholds. Gascoigne et al. (2009) point out that there are two main categories of adaptations to mitigate mate-finding Allee effects: mechanisms that increase the efficiency of mate-finding at low density such as calls or chemical signalling (e.g., bioluminescent signalling of deep sea fishes: (Ruxton and Bailey 2005), and mechanisms that reduce the likelihood of low density such as mass spawning (e.g., spawning aggregations of cod: Skjraasen et al. 2011). While mass aggregation may be disrupted at very low density (Reed and Dobson 1993; Rowe and Hutchings 2003), some mate-finding strategies such as pheromone signalling can be quite effective at small population size.

Mate-finding strategies which rely on landscape cues may also be effective at low population density. Rather than being attracted by signalling cues from the opposite sex, individuals may simply move towards particular locations in the landscape which can either be detected from long distances (landmarks such as treetops and hilltops: Thornhill and Alcock 1983), or which have previously known coordinates (e.g., site fidelity to mating grounds of the albatross: Dubois et al. 1998). For example, it is estimated that over 1000 insect species find mates at the prominent conical hilltop Mount Morris, Queensland, which rises 350 m above the surrounding area (Skevington 2008). Of these two versions of landscape-determined mate-finding strategies, the use of landmarks, rather than previous knowledge of mating grounds, will be more robust to low densities, since loss of population density can be associated with a loss of the knowledge or individual use of specific mating grounds (Frank and Brickman 2000). Certainly, the use of prominent landmarks is most relevant to the spread of invasive species, since newly introduced individuals will have no previous knowledge of the landscape.

When population density is low, we may guess that if there are only a few landmarked mate-finding sites over a large area, it is quite unlikely that a male and female may end up at the same location at the same time. For example, there is currently concern that Asian carps of the genus *Hypophthalmichthys* (Bighead and Silver Carps) may colonize the Great Lakes system (Cudmore et al. 2012). These types of Asian carps require rivers of sufficient size and flow for successful spawning (Costa-Pierce 1992; Kolar et al. 2005), but there are relatively few such rivers on each of the Great Lakes. Kocovsky et al. (2012) identify three rivers connected to Lake Erie as good spawning habitat, and suggest a further three may also have potential. The fact that so few suitable rivers have been identified has led some to suggest that it is unlikely that successful reproduction could take place at low density.

Here, we explain why this intuition regarding the Allee effect and the scarcity of mate-finding sites may be in error. We begin from the position that the encounter probability of a male and female at a mating location can be viewed as a variant of the birthday paradox: the calculation of the probability that at least two people in a group of randomly selected individuals will share the same birthday (Feller 1957). This probability is of importance when calculating quantities in widely various applications such as the probability that airplanes will collide, or that there are matches between random length clone fragments in DNA mapping (Soderlund et al. 2000), and has been used in the past to estimate fish population sizes (Schnabel 1938). The birthday paradox is not a true paradox; however, the finding that a group of only 23 people is required to have a greater than 50 % probability that two share a birthday is a surprise to many. This difficulty with intuition most likely relates to the fact that the birthday paradox asks whether any of the people in a given group has a birthday matching any of the others, not one in particular. As a result, in this small group of people, there are over two hundred combinations to consider.

In the following, we examine how the use of a small number of landmarked sites might impact the distribution of individuals, and therefore the probability of mate-encounter. We begin by comparing the expected distribution of individuals which have an aggregative tendency with the expected distribution for individuals using only landmarking. We use a calculation similar to that of the birthday problem to determine the probability that at least one mate encounter could occur for a given number of landmarked sites. However, since we have two sexes, it is necessary to use a modification of the birthday problem where there are two classes of individuals (Wendl 2003; Nakata 2008). Using this modification, we consider the effect of sex ratios on the mate encounter probability, and the impact of different mating strategies (monogamy vs. polygyny) on the estimated number of mated females. Since the combinatorially exact calculations require lengthy computations, we also evaluate a number of different approximation methods for estimating the number of mated females.

Unlike the birthday problem where all individuals must have a birthday, not all individuals may arrive at a landmarked site. Although many species travel long distances to arrive at landmarked sites (Skevington 2008), some sites may be too distant for detection, or individuals may inaccurately identify suitable sites. For example, Pe’er et al. (2004) found that butterflies in the vicinity of multiple peaks typically select the highest within visual range (approximately 50 m). We should expect that mating probability will be reduced if only a small proportion of the sexually active population manages to arrive at landmarked sites. Therefore, we also examine the impact of site-finding success rates on the predicted number of mated pairs.

Finally, using these approximations and simulation data, we examine the potential impact of the landmarking strategy on the strong Allee threshold. For some applications, such as predicting the risk of invasion, an impact of landmarking on a strong Allee threshold could be relevant for determining whether a given management strategy is feasible.

## Modelling the effect of landmarked mate-finding sites on Allee thresholds

### Attraction to conspecifics versus random assortment among landmarked sites

We begin our exploration of the impact of a landmarking strategy on mate encounter by first noting that there is a difference in the expected distribution of individuals where there is a tendency to be attracted to higher densities of conspecifics (e.g., the mating aggregations mentioned by Gascoigne et al. (2009)), versus only attraction to landmarked features. If individuals are equally attracted to all landmarked sites and have a reasonable probability of travelling to any site, they will be less aggregated, and have a lower probability of finding a mate than when there is strong attraction to high-density groups of conspecifics. However, for either strategy, we expect a larger number of male–female pairs when there are fewer mate encounter sites.

An aggregative tendency will produce higher local densities of individuals. If males and females respond directly to the density of conspecifics (but not the sex-ratio), we can simulate their distribution across the mate-finding sites using two sets of 8 random numbers drawn from the negative binomial distribution (Boswell and Patil 1970). Depending on the strength of the attraction, individuals will collect at one or very few sites, and consequently nearly every individual may find a mate (Fig. 1b, c). However, when there are more possible sites, the probability of males and females occupying the same location is somewhat reduced even with this aggregative tendency (compare Fig. 1b with e, and c with f).

In summary, when individuals are not attracted to higher densities of conspecifics, their distribution is predictably less aggregated (compare Fig. 1a with c and b). Therefore, the assumption that individuals are only attracted to landmarked sites and not conspecifics will lead to lower estimates for the probability that individuals will successfully find a mate. It is this more conservative scenario that we address in the following work, but we note that the positive impact of fewer mating sites on mating probability will be similar for species with conspecific attraction, although it will be of much smaller magnitude.

### The probability of at least one successful mating

If mate-finding sites such as hilltops, tall trees or large rivers have long range detectability, and are within reasonable travel distance, then the main barrier to a successful reproductive event is that a male and female will be present at the same location. Here, we calculate the probability of at least one mate encounter for a given number of landmarked sites, and numbers of males and females. This probability has some useful interpretations. When developing policies regarding a potentially invasive species, if even a single mating is quite unlikely for a given density, then the potential invasive may represent very low risk. Similarly, an endangered species is probably beyond all recovery if even a single mating becomes quite unlikely.

The encounter probability of a male and female individual at a mating location can be viewed as a variant of the birthday paradox. However, rather than just calculating the probability that two individuals will share a category as in the birthday paradox, we have two kinds of individuals in our problem: males and females. To address this complication, we use more recent work that addresses the probability that two different kinds of objects end up in the same bin (Wendl 2003; Nakata 2008). To apply this probability to mate-finding, we consider that our two kinds of objects are males and females, and the bins are those locations where individuals go to seek mates (e.g., spawning rivers, hilltop sites). If we assume that encounters between males and females are unproblematic once at a mate-finding site, and furthermore, that individuals are ready for mating at about the same time, we can show that the probability of at least one mate encounter is quite likely at very low population density.

*P*

_{0}), and then use one minus this probability (1−

*P*

_{0}) to determine the chance that there is at least one mate encounter. Following Wendl (2003), we can calculate the exact probability that there are no simultaneous occurrences of male and female individuals in the same mate-finding location as:

*m*is the number of males,

*f*is number of females,

*r*is the number of mate-finding sites, and

*S*

_{2}refers to Stirling numbers of the second kind. So,

*S*

_{2}(

*n*,

*k*) represents the number of ways we can partition

*n*individuals into

*k*groups. We assume that the distribution of males is independent of the distribution of females, so that

*r*

^{ m+f }gives the total number of ways of arranging the males and females among

*r*landmarked sites. When considering the probability of no encounter events, we are interested in the number of these arrangements that result in no female arriving at a site with a male. For example, there are 16 ways to arrange 2 males and 2 females across 2 sites, but only 2 of these arrangements isolate females from males (see Appendix A). The probability that there is at least one meeting of a male and female in the same location is then given by 1−

*P*

_{0}.

### Estimated number of matings

We have estimated the probability of at least one mating in a small population using a landmarking strategy. For potentially invasive species, if the probability of mate encounter is very small over the probable range of introduction densities, our management concerns may end there. If, however, there is a reasonable chance of a single mating (say greater than 50 %), the next question to ask is how many mated females should we expect.

An exact calculation for the expected number of matched monogamous pairs (or the related measure, the probability that a female will be mated) was offered by Wendl (2005), in the context of DNA fingerprinting. In our context, the number of mated monogamous pairs is \(k={\sum }_{i=1}^{r}min(m_{i}, f_{i})\), where *m* _{ i } and *f* _{ i } are the number of males or females at location *i*, and there are *r* total landmarked locations. As noted by Wendl (2005), the exact solution to the problem rests on a calculation of the number of ways the sets of all males and all females can be partitioned into groups, and these groups of different sexes distributed across the landmarked sites. This exact calculation is quite lengthy, and for an intermediate to large number of landmarked locations, takes considerably more computer processing time than a simple simulation. Moreover, there is excellent agreement between simulation and the exact calculation (see Appendix B). Therefore, we report the simulated results here.

*i*, we expect 46 mated pairs, whereas for 20 possible locations, we expect only 33. Instead of monogamous pairing, we could assume that one male can fertilize all females at his location (complete polygyny). In this case, the maximum expected number of mated females is a higher proportion of the number of females at mate-finding sites than in monogamous mating, but the same general relationships apply.

### Probability of site-finding

The previous calculation is based on the total number of individuals in a population and assumes that all individuals arrive at a landmarked site. Here, we investigate the consequences of relaxing that assumption for the predicted number of monogamous mated pairs. It is certainly possible that only a portion of the population is successful at locating landmarked sites. For example, not all fish present in the lake may arrive at suitable spawning rivers, or fish may incorrectly identify rivers as suitable. If some individuals do not actively seek out mate-finding sites or if the landmark cues are imperfect and lead to the selection of an unsuitable location, then the number of individuals that are matched with a site will be smaller, and the probability of finding a mate, given as a function of total population density, will be lower.

One simple way to approach difficulties in locating landmarked sites is to multiply our total number of sexually active adults by a given probability of encountering an appropriate location during the correct environmental conditions. If we take a low but not restrictive value of 20 % of the population meeting this criteria, then we can use the previous calculation to determine the probability of one successful encounter. If 20 % of a population of 50 males and 50 females (or 1 % of a population of 1000 males and 1000 females, 10 % of a population of 100 males and 100 females, etc.) were successful at finding mating locations, then the predicted number of successful pairs would be the same as the probability based on the expected number of 10 individuals of each sex that arrive at landmarked sites (Fig. 3a).

If, however, the total number of individuals that arrive at any landmarked site is a positive function of the number of locations, the situation may change. For example, we could use a saturating function to describe the probability that an individual arrives at a mate-finding site. The function *f*(*r*)=*r*/(*r* _{0}+*r*) ranges from 0 to 1, where the value of the function increases to the asymptote of 1 as *r*, the number of landmarked sites, increases. The number of individuals that successfully locate a site is then calculated as the number of individuals in the population multiplied by the value of *f*(*r*). In this case, the probability of one successful encounter at low population size can be highest for an intermediate number of mate-finding sites. As a result, we expect a larger number of mated pairs at an intermediate number of sites (the position of the peak will be determined by the half-saturation constant). That is, the difficulties of arriving at a mate-finding site when there are few of these sites will be offset by the problem of few or no individuals at each location when the number of sites is very large (Fig. 3b). This result depends on the value of the half-saturation constant, *r* _{0}. As *r* _{0} approaches zero, we regain our original result (Fig. 3a), but as *r* _{0} becomes large, a larger number of mate-finding sites are required to have some significant probability of one successful encounter at low density.

### Approximating the effect of landmarking strategies on mate-finding

These exact solutions, or equivalent simulated solutions, are cumbersome for calculations regarding population dynamics. We would like simpler formulas to approximate the exact solutions for the expected number of mated females. For monogamy and a one to one sex ratio, one of the most commonly used equations to predict the probability that a female will find a mate is *m*/(*m*+*𝜃*) (1), where *m* is the number of males in the population and *𝜃* expresses factors that determine the search success (e.g., Dennis 1989; Veit-and-Lewis 1996). In other work (Cuddington et al. 2014), we have also used a normal approximation as: \(m-\sqrt {m(\theta -1)/\pi }\) (2), where again we assume an equal number of males and females (see derivation and more general cases in Walter (1980)). For polygyny, 1−*e* ^{−m/𝜃 } (3) is often used (e.g., Dennis 1989; Hopper and Rousch 1993), but we could also use a binomial approximation, where the probability of a female mating is 1−(1−1/*𝜃*)^{ m } (4; see derivation in Appendix A). For our landmarking strategy, in all these equations, *𝜃* is the number of mate-finding locations, *r*.

Unlike the exact solution (Appendix B), to approximate the number of mated pairs, we assume that the probability of one female mating is independent of the probability that another female mates. So, to calculate the expected number of mated females, *E*(*P*), we simply multiply this probability by the number of females. However, if not all males and females locate a site, we need to correct values of both *m* and *f* so that they express the number of males or females that locate mate-finding sites rather than total number of each sex in the population. For example, where site-finding is a saturating function of the number of sites, *r*, the actual number of males, *m*, at landmarked sites will be *m* _{ s i t e s } = *m* _{ t o t a l }∗*r*/(*r*+*r* _{0}).

*m*/(

*m*+

*𝜃*) performs reasonably well but will generally overestimate the mean number of pairs (maximum overestimate 3.57, minimum underestimate 0.98, Fig. 4a), except in the case of a single mate-finding site. Walter’s normal approximation will consistently underestimate the number of mated females (maximum overestimate 0, minimum underestimate 4.33, Fig. 4b). However, neither of these approximations is appropriate for polygyny (Fig. 4e, f).

Unsurprisingly, given the strongly conditional nature of the exact solution, the poisson (3) and the binomial approximations (4) are not good for monogamy, producing a consistent overestimate ranging up to 13 pairs (Fig. 4c, d). However, for polygyny, these two approximations perform the best of the four investigated and are only slightly biased to underestimate the number of mated females. The binomial approximation has a modestly superior performance (maximum overestimate 0.034, minimum underestimate 0.069, Fig. 4h), compared to the poisson approximation (maximum overestimate 0.001, minimum underestimate 0.37, Fig. 4g).

### Threshold for strong Allee effect

Finally, we can describe how the landmarking strategy might affect population dynamics by determining its impact on a strong Allee threshold. If the per capita population growth rate is given by the number of births minus the number of deaths as (*b* *E*(*P*)−*d* *N*)/*N*, where *E*(*P*) is the expected number of mated females estimated as above, *b* is the recruitment rate per mated female, and *d* is the per capita death rate, then we can solve for the population density at which this rate is equal to zero to generate a function describing how the Allee threshold changes with the number of landmarked sites (in practice, these functions are generally implicit equations).

*r*

_{0}, is small, the Allee threshold is extremely large for very few sites, but drops rapidly for an intermediate number of sites (Fig. 5b). Of course, when the proportion of the population that locates landmarked sites increases quite slowly as the number of sites increases (large

*r*

_{0}), the number of sites that produces the minimum Allee threshold will increase.

## Discussion

Many species may employ strategies that mitigate mate-finding component Allee effects via a restriction on the number of locations where individuals search for mates (e.g., Shields 1967; Wickman 1988; Mills 1989). The use of particular ‘landmarked’ mate-finding locations sometimes can be distinguished from the occurrence of mating in areas that are likely to boast nesting areas and resources for successfully rearing offspring. The best known instance of this behaviour is hilltopping in butterfly species where males and females use topographical cues to aggregate at areas of high elevation (e.g., Pe’er et al. 2004). Hilltops are not the only features used for this strategy. For example, using plastic spruce tree models of different heights, Wickman (1994) demonstrated that *Coenonympha pamphilus* male butterflies and virgin females were attracted to the tallest trees in an open grassland. Skevington (2008) defines a landmark mating strategy as setting up mating aggregations over any landscape feature, where such features can include a tuft of grass, a stream course or a hilltop. These areas do not necessarily have host plant species for either larval or adult life stages. It is generally accepted that the use of these areas is a behavioural mechanism to increase mate encounter rate (Shields 1967; Scott 1970), and recently sophisticated simulation models have corroborated the theory that hilltopping can improve butterfly mating success at low density (Pe’er et al. 2006; Painter 2014). In other systems, the use of a restricted number of mating locations may be combined with access to resources necessary for successful maturation of offspring (e.g., brook trout, see Purchase and Hutchings 2008). In addition, some mating behaviours, such as lekking, are primarily examined in light of questions regarding sexual selection (e.g., bower-building cichlid fish see Young et al. 2009) but may have impacts on mate encounter probability.

All these landscape-related strategies may have the effect of increasing the probability of mate encounter over what would be expected during the non-breeding distribution of individuals. Our calculations suggest that such behaviours are an extremely efficient way to increase mate encounter when there are relatively few such sites. Attraction to landmarked sites will never produce the same concentration of density as strong attraction to high density of conspecifics. Nonetheless, when there are few such sites, landmarking may be a highly efficient method of clustering individuals. Indeed, landmarking is potentially more efficient than conspecific attraction that produces mating aggregations, which is disrupted at very low density (e.g., Rowe and Hutchings 2003). A combination of landmarking and attraction to conspecifics will be even more efficient.

We find that a landmarking strategy can lead to high mate encounter probability at low density, which has some unexpected management implications for both invasive and endangered species. In general, the fewer the number of landmarked locations, the larger the probability of at least one mating. Therefore, the expected number of mated females is greatest, and the strong Allee threshold is smallest, for the fewest number of landmarked sites. Superficially, this finding may seem counter-intuitive, but it is well known that intuitions about probability and risk are not always reliable (e.g., Kahneman et al. 1982). This seems to be particularly true when our probability calculation involves combinatorics: a counting up of the number of ways in which an event can occur. For example, managers may believe that if a small number of Asian carps escape into a Great Lake, such as Erie, they are unlikely to establish a population because it will be difficult to find a mate. Our calculation, using a variant of the birthday paradox, demonstrates that this intuition is probably false. Indeed, using a spawning-river structured model, Cuddington et al. (2014) found that the limited number of suitable rivers increased the probability of a successful Asian carp invasion.

Of course, not all individuals may be successful at finding a landmarked mating site. We expect that species invading new areas may have difficulty locating or identifying suitable sites. Butterflies may select the highest hilltops within visual range (Pe’er et al. 2004), and therefore may not locate higher, but more distant peaks. Asian carp can be triggered to spawn by warm water temperature and high flow rate (Costa-Pierce 1992; Kolar et al. 2005), but may be unable to determine if a river is of sufficient length for successful reproduction. It could be that only some small percentage of individuals find a suitable landmarked site, in which case the probability of a single mating event is somewhat reduced, but is still highest for the smallest number of landmarked sites. Alternately, the probability of finding a suitable location could increase at a decreasing rate with the number of such sites. In the latter case, the probability of at least one successful mating when the population size is small will also depend on how quickly search success increases with the number of locations. In general, the largest probability will be found for an intermediate number of landmarked sites (Fig. 4) and as a result, population growth will be positive for an intermediate number of sites, rather than for a larger number, as intuition might suggest (Fig. 5).

However, as we note, some landmarked sites may be more accessible or more detectable than others, and we did not explicitly include this factor in our analysis. Differing accessibility is different than some sites being preferred to others when all have equal accessibility. In the case of simple preference, a larger number of individuals will collect at the highly preferred sites, and mate-finding would be more probable (i.e., similar to the case when individuals are attracted to high densities of conspecifics, Fig. 1). In the case of differing accessibility or detectability, it may be more difficult to travel to or to locate some particular sites. For example, when a non-native species is introduced, very few individuals may reach sites distant from the initial point of introduction. In this case, the accessibility of sites would change through time as the individuals reproduced and spread through the landscape. Therefore, we suggest that initially, there would be a greater probability of at least one mating, as individuals would make use of the smaller number of mate-finding sites in their immediate vicinity.

The ratio of females to males in the population can also alter the probability of at least one successful mating (Fig. 2), but does not have a large effect until sex ratios are seriously skewed. Of course, males and females may arrive at a mate-finding location at different times. If individuals will only wait to encounter the opposite sex in a given location for a small time interval, the probability of successful mating will be further reduced. However, even for this scenario, a simple calculation using Wendl’s formula (2003) shows that the probability of at least one successful mating is still quite large (e.g., 75 % for 10 females and 10 males and 60 time/space intervals). Of course, if individuals only briefly visited mate-finding sites, and there were an even larger number of mating sites, this probability would be reduced (i.e. we would have a very large number of space/time intervals). However, in some species, males linger in the landmarked location for longer periods of time, which would of course increase mating success (e.g., Rutowski 1991).

Simulations provide an extremely good approximation to the expected number of mated females in the scenarios we investigated, and are quite useful given the lengthy calculations required for the exact solutions (Appendix B). However, simpler equations can also be used to approximate the exact solutions, and some are reasonably accurate for polygyny. The standard equations we tested for monogamy over- or under-estimated the number of mated pairs in particular ranges. When using such approximations, we need to be cognisant of the direction of bias. For example, a commonly used estimate from the literature (1: *m*/*m*+*θ*) when applied to landmarking will consistently overestimate the number of mated pairs when there is modestly high population size and few sites. However, this approximation is more accurate for low population size and a larger number of sites. As a result, we suggest the use of this equation when generating optimistic estimates of extinction risk. Walter’s (1980) normal approximation (2) underestimates the number of pairs at low population density and many sites. Therefore, the normal approximation would be an optimistic estimate of risk for potentially invasive populations, and a pessimistic estimate of extinction risk.

When attempting to determine if a demographic mate-finding Allee effect occurs for endangered or invasive populations, we need to be careful when the organisms in question use a restricted number of mate-finding locations. This is particularly true because mechanisms such as true aggregation are disrupted at low density, while attraction to landmarked sites is unaffected by density. Conservation programs may take advantage of the mate-finding at landmarked sites. Reintroduction efforts typically rely on the release of a sufficient number of individuals such that enough will survive to breed and re-establish a population (Rakes et al. 1999; Daugherty et al. 2008). Our analysis suggests that for some species (e.g., salmonids, sturgeon), this effort may be hampered by the creation of too much, overly fragmented, mating habitat. A large number of small and diffuse mating locations could require the release of a larger number of individuals to achieve positive population growth. Fewer mate-finding locations could initially concentrate individuals and thus maximize mate-pairings and fertility at lower release densities. Of course, the use of such a strategy must be balanced against the potentially large negative consequences that might ensue when environmental stochasticity or human impacts impinge on one of a few landmarked sites. Given the risks, clearly one would want experimental data that confirms much higher mating success with fewer landmarked sites before implementation.

Estimation of risk of establishment of non-native species, and management of established invasive species, is often predicated on the presence of Allee effects. For example, the release of sterile males in biological control (e.g., Knipling 1955; Twohey et al. 2003) is aimed at reducing the number of successful matings, and therefore, pushing the per capita population growth rate to zero. While this type of strategy is undeniably useful for many species, we urge caution when applying this reasoning to species that use a restricted number of mate-finding sites. The use of landmarked sites does not necessary produce large densities of individuals at a given location, but it can certainly increase the probability that a male and female meet, even when there is no prior knowledge of particular landmarks. Certainly, landmarking species can be successful invaders (e.g., Braby et al. 2014). Our examination of this issue suggests that when a strong Allee threshold exists for these types of species, it may be very small indeed, and unlikely to be reached via management aimed at reducing the number of viable males. Moreover, control actions that focus on reducing suitable mating habitat in an effort to reduce reproduction may have the opposite of the intended effect depending on search strategies and the current number of landmarked locations. We conclude that such ‘landmarking’ is a frequently overlooked mating strategy that should be accounted for when predicting invasion risk.

## Notes

### Acknowledgments

This work was supported by Fisheries and Oceans Canada.

### **Open Access**

This article is distributed under the terms of the Creative Commons Attribution License which permits any use, distribution, and reproduction in any medium, provided the original author(s) and the source are credited.

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