induced dispersal in wildlife management: experimental evaluation of the risk of hybrid breakdown...
TRANSCRIPT
RESEARCH ARTICLE
Induced dispersal in wildlife management: experimentalevaluation of the risk of hybrid breakdown and the benefitof hybrid vigor in the F1 generation
Clare E. Holleley Æ Richard A. Nichols ÆMichael R. Whitehead Æ Melissa R. Gunn ÆJyoutsna Gupta Æ William B. Sherwin
Received: 6 April 2009 / Accepted: 29 August 2009 / Published online: 16 September 2009
� Springer Science+Business Media B.V. 2009
Abstract Management practices often aim to increase the
level of gene flow by either: introducing animals from
captive breeding programs, translocating animals from
abundant areas, or increasing the chance of animals dis-
persing between populations by creating habitat corridors.
These practices provide opportunity for the hybrid off-
spring of introduced and resident animals to experience
either increased fitness (hybrid vigor) or decreased fitness
(hybrid breakdown). There is very little quantitative data
available to adequately assess whether hybridization is
likely to be beneficial or detrimental to populations
managed in these ways. Using Drosophila melanogaster
populations, we conducted two experiments that simulate
the common management practices of translocation and
wildlife habitat corridors. We monitored the frequency and
magnitude of hybrid vigor and hybrid breakdown in F1
hybrids to assess the relative risks and benefits to popula-
tions and also monitored net productivity (number of adults
produced from controlled crosses) to assess whether the
populations were stable or in decline. In the translocation
experiment, we observed instances of both significant
hybrid vigor and hybrid breakdown, both occurring at a
frequency of 9%. In the habitat corridor experiments,
populations with moderate to high dispersal (1–4% per
generation) did not develop significant hybrid vigor or
hybrid breakdown. However, of the populations experi-
encing low dispersal (0.25% per generation) for 34 gen-
erations, 6% displayed significant hybrid vigor and 6%
displayed significant hybrid breakdown. These results
suggest that in first generation hybrids there may be limited
opportunity to utilize hybrid vigor as a tool to increase the
short-term viability of populations because there is an
equal likelihood of encountering hybrid breakdown that
may drive the population into further decline. However,
our results apply only to populations of moderate size
(N = 50; Ne = 14.3) in the absence of deliberate consan-
guineous mating. Lastly, we observed that net productivity
was positively correlated with dispersal rate, suggesting
that initial F1 declines in fitness may be temporary and that
it is preferable to maintain high levels of selectable vari-
ation via induced dispersal to assist the long-term survival
of vulnerable populations.
Keywords Hybrid vigor � Hybrid breakdown �Inbreeding depression � Drosophila melanogaster �Conservation � Management � Genetic drift
Electronic supplementary material The online version of thisarticle (doi:10.1007/s10592-009-9984-z) contains supplementarymaterial, which is available to authorized users.
C. E. Holleley � M. R. Whitehead � M. R. Gunn � J. Gupta �W. B. Sherwin
Evolution & Ecology Research Centre and School of Biological,
Earth & Environmental Sciences, University of New South
Wales, Sydney, NSW 2052, Australia
R. A. Nichols
School of Biological and Chemical Sciences, Queen Mary
University of London, Mile End Road, London E1 4NS, UK
M. R. Whitehead
Botany and Zoology, School of Biological Sciences, Australian
National University, Canberra, ACT 0200, Australia
M. R. Gunn
Food and Environment Research Agency, Sand Hutton, York
Y041 1LZ, UK
C. E. Holleley (&)
Laboratory of Genomic Diversity, National Cancer Institute,
Frederick, MD 21702, USA
e-mail: [email protected]
123
Conserv Genet (2011) 12:31–40
DOI 10.1007/s10592-009-9984-z
Introduction
Population fragmentation is a major contributing factor to
the risk of population extinction in the wild (Tilman et al.
1994; Henle et al. 2004; Reed 2004). A consequence of
habitat fragmentation is that dispersal and gene flow are
limited between populations. Management practices are
often designed to increase the level of gene flow in remnant
populations by either: introducing animals from captive
breeding programs (Seddon et al. 2007), translocating
animals from abundant areas (Miller et al. 1999) or
increasing the chance of animals dispersing between pop-
ulations by creating habitat corridors (Beier and Noss
1998). These induced dispersal methods ultimately aim to
reduce the probability of population extinction by
increasing local population sizes and alleviating any neg-
ative effects of inbreeding depression (Frankel 1983; We-
stemeier et al. 1998; Vila et al. 2002; Pimm et al. 2006).
However, another consequence of induced dispersal is that
distantly related populations can begin to hybridize, pro-
ducing a spectrum of fitness outcomes in the offspring,
from hybrid vigor to hybrid breakdown.
Our working definitions of hybrid vigor and of hybrid
breakdown are respectively, any increase or decrease in the
fitness of hybrids between lineages that have experienced
periods of separate evolution (Ehiobu and Goddard 1990a,
b). In practical terms we expect lineages that have experi-
enced periods of separate evolution to display significant
genetic population structure and in this study we deal with
periods of separate evolution that would be discernable on a
management timescale, for example tens of generations.
Hybrid vigor, where hybrid individuals experience higher
fitness than observed in the two parental populations, has at
least two explanations. Firstly, hybrid vigor can be a result of
the alleviation of inbreeding depression when deleterious
recessive alleles are masked in the highly heterozygous
hybrid (dominance and overdominance; Crow 1948; Birch-
ler et al. 2003). Secondly, hybrid vigor can occur in the
absence of inbreeding due to the formation of novel genetic
interactions in the hybrid (Whitlock et al. 2000; Birchler
et al. 2003). There have been several examples where hybrid
vigor appears to have been exploited successfully to manage
vulnerable populations, such as the Florida panther (Pimm
et al. 2006) and the Scandinavian grey wolf (Ingvarsson
2002). In contrast to these examples, induced dispersal can
also result in negative conservation outcomes if the hybrid
offspring are less fit than the offspring of the parental lines, a
phenomenon called hybrid breakdown (Wallace 1968).
Hybrid breakdown can be a consequence of chromosomal
rearrangements (Fishman and Willis 2001), disruption of co-
adapted gene complexes (Templeton 1986), underdomi-
nance (Schierup and Christiansen 1995) or interaction
among genomic elements (Rhode and Cruzan 2005). Cases
that unequivocally link hybrid breakdown with increased
susceptibility to extinction are rare and poorly documented
(Turcek 1951) but there is a large body of evidence sug-
gesting that genetic differentiation can result in hybrid
breakdown and that this process can occur rapidly (Kidwell
and Novy 1979; Boussy and Kidwell 1987; Lozovskaya et al.
1990).
To correctly manage the risk of hybrid breakdown and
the opportunity of hybrid vigor, the manager of a wild
population needs to know the probability of each of these
outcomes. Given that the managers usually only have very
few populations, any appreciable chance of adverse out-
comes must be very carefully managed and a precautionary
approach applied. Induced dispersal is sometimes consid-
ered to be a low risk conservation strategy because hybrid
breakdown is assumed to occur less frequently than hybrid
vigor (Edmands 1999), however, there is very little quan-
titative data to support this assumption (Moll et al. 1965;
Ehiobu and Goddard 1990a). Conversely, wrongly assum-
ing that hybrid breakdown is widespread and common may
result in overly restrictive management strategies that
exacerbate the negative effects of fragmentation. In either
case it is imperative to obtain quantitative information that
evaluates the risks versus benefits involved with induced
dispersal. The large body of literature available on hybrid
vigor and breakdown generally focuses upon the recovery
of populations in which there has been deliberate consan-
guineous mating and/or extremely small effective popula-
tion sizes (total population size N = 2–8), conditions
which are appropriate to critically endangered species
(Spielman and Frankham 1992; Backus et al. 1995; Ball
et al. 2000; Marr et al. 2002). However, there is little
information about the inherent frequency of hybrid vigor
and breakdown under conditions experienced by wild
managed populations that have not reached this threshold
of extinction risk, and thus have not experienced enforced
consanguineous mating and have moderate to small
effective population sizes. Additionally the current litera-
ture typically assumes that populations are completely
isolated and ignores the effects of ongoing low-level dis-
persal (Loebel et al. 1992; Bryant et al. 1999; Reed 2005),
a scenario that is often a more realistic representation of
wild populations.
In this study we conducted two replicated, controlled
experiments in moderately sized populations of Dro-
sophila melanogaster that aimed to evaluate the relative
risks and benefits of current management practices in the
absence of deliberate consanguineous mating. The first
experiment simulated translocation practices, where we
investigated the occurrence of hybrid vigor and hybrid
breakdown among fragmented populations that had
experienced an extended period of complete isolation
(zero gene flow). The second experiment simulated
32 Conserv Genet (2011) 12:31–40
123
habitat corridors, where we investigated the occurrence of
hybrid vigor and hybrid breakdown in fragmented popu-
lations that experienced low levels of gene flow. In each
experiment our general aim was to evaluate the risk of
hybrid breakdown impairing conservation efforts, relative
to the benefit of hybrid vigor. For populations that are
large enough to have avoided the fixation of deleterious
alleles we predict that the major mechanism of population
differentiation is the action of genetic drift to change the
frequency alleles at polymorphic loci. Depending on the
fitness effects of the alleles that happen to drift to higher
frequency, both hybrid vigor and hybrid breakdown could
occur. Consequently, we formulated and addressed the
following two hypotheses. Firstly, we predicted that
periods of population isolation (translocation experiment)
or restricted dispersal (corridor experiment) would result
in significant hybrid vigor or hybrid breakdown in the F1
generation. Our second hypothesis predicted that, since
these were not severely inbred lines (in either the trans-
location or the corridor experiment), the frequency and
effects of hybrid breakdown would be of the same order
as hybrid vigor, hence both phenomena should be
detectable in some replicates.
Materials and methods
Construction of the metapopulation
Both the translocation experiment and the habitat corridor
experiment involved studying the effects of fragmentation,
thus we first had to create an artificially fragmented
metapopulation that was the starting point for both exper-
iments (Fig. 1). The source population of D. melanogaster
was a large wild population, collected from Tyrell’s Win-
ery, Hunter Valley, New South Wales (Australia) in April
2000. Wild caught individuals were used to establish 12
smaller laboratory populations (referred to as lines),
founded by 100 males and 100 non-virgin females. The 12
laboratory lines were maintained at large population sizes
(C200 individuals), with zero gene flow for 50 months
(*60 generations). All lines were maintained on an instant
potato-sugar artificial insect food medium (Holleley et al.
2008). This manipulation simulated an episode of frag-
mentation where a large population was reduced into
genetically isolated sub-populations for an extended period
of time. To quantify the effect that the imposed fragmen-
tation had on the level of genetic differentiation, we gen-
otyped 20 individuals per line at six autosomal
microsatellites (England et al. 1996; Gunn 2003) and
estimated the mean pair-wise fixation index FST (Weir and
Cockerham 1984).
Experiment 1: Translocation
Using the artificially fragmented metapopulation, we sim-
ulated translocation by allowing reproduction between
previously genetically isolated lines (Fig. 1). We used the
results of controlled crosses to estimate the mean hybrid
performance statistic (Hij). See below for crossing meth-
odology and calculation of Hij. Investigating Hij in all 132
pair-wise combinations of lines within the artificial meta-
population was prohibitive, thus we chose a subset of 11
line pairs for detailed investigation (line pairs: 1_11, 1_4,
5_11, 9_11, 18_20, 5_22, 17_21, 18_22, 1_22, 18_21).
Using the observed magnitude and frequency of Hij in the
11 line pairs, we tested our two hypotheses and evaluated
the risk of hybrid breakdown versus the benefit of hybrid
vigor in translocation practices.
Experiment 2: Habitat corridors
In natural populations habitat corridors are tracts of land or
bodies of water that connect geographically and genetically
isolated populations. Corridors aim to encourage dispersal
Tyrell’s Winery Large, wild, panmictic population
Artificially Fragmented Metapopulation
100 males 100 females collected from wild to establish each Lab Line
Expt.1: Translocation Expt.2: Habitat Corridors
1 Isolated
Lab Lines FST = 0.08 ± 0.01SE 12
3 4 5 9
22 11
17
18
20
21
1 11
1 4
Zero gene flow between lines for ~ 60 generations
3 4
17 21
3 3
17 17
Genetically differentiated line pairs:
FST = 0.2 ± 0.01SE ~60 generations of isolation
Genetically similar line pairs:
FST = 0.01 ± 0.006SE 1 generation of isolation
Conduct crosses as in Fig. S1 and estimate Hij
H1_11
Low levels of dispersal through the corridors
(m = 0.04, 0.01, 0.0025)
H1_4
5 11 H5_11
9 11 H9_11
18 20 H18_20
5 22 H5_22
17 21 H17_21
18 22 H18_22
1 22 H1_22
18 21 H18_21
m
m
m
m
Low levels of dispersal through the corridors
(m = 0.04, 0.01, 0.0025)
Conduct crosses as in Fig. S1 and estimate Hij, at three sampling times:
T0, T1 & T2 (see Table 1)
(X 4)
(X 4)
(X 4)
(X 4) 3 4 H9_11
Fig. 1 Experimental design flow diagram. Illustrates the construction
of the artificial metapopulation which was subsequently used to
investigate the frequency and magnitude of hybrid vigor and hybrid
breakdown under two induced gene flow management practices:
translocation (Experiment 1) and habitat corridors (Experiment 2)
Conserv Genet (2011) 12:31–40 33
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and gene flow between populations. To simulate the effects
of habitat corridors we allowed a low level of dispersal (m)
between previously isolated pairs of populations (Fig. 1).
We commenced the habitat corridor experiment using four
lines from the artificially fragmented metapopulation
(lines: 3, 4, 17, and 21). These lines were chosen for use in
Experiment 2 because they showed a mean Hij closest to
zero in a preliminary low replication screening of line
pairs. This screening step was imperative to avoid selecting
lines for Experiment 2 that already showed a significant
Hij, which would then bias the subsequent experiment
towards either positive or negative Hij (low replicate
screening data not shown, refer to Fig. 2 for high replicate
data). The dispersal schemes were designed to simulate two
scenarios: firstly induced gene flow between pairs of
genetically differentiated populations (line pairs: 3_4 and
17_21) and secondly induced gene flow between pairs of
recently isolated genetically similar populations (line pairs:
3_3 and 17_17). The effect of restricted dispersal on
genetic differentiation was quantified by genotyping 24
individuals per population at seven autosomal microsatel-
lites (Holleley 2007; Holleley and Sherwin 2007) and
estimating FST (Weir and Cockerham 1984). The geneti-
cally differentiated line pairs were selected such that
FST = 0.2 ± 0.01 SE (P = 0.001). Genetically similar
line pairs (3_3 and 17_17) were constructed by splitting
lines 3 and 17 after the 50-month period of isolation and
thus these line pairs did not significantly differ from an FST
of zero (FST = 0.01 ± 0.006 SE; P = 0.268). All lines
were maintained with a constant population size of 25
males and 25 females, which corresponds to an eigenvalue
effective population size (Ne) of 14.3 (Gunn 2003; Gilligan
et al. 2005; Holleley 2009). We allowed founding indi-
viduals to mate randomly for 7 days, after which we
removed the adults for the proliferation of the next discrete
generation. We randomly chose 25 males and 25 non-vir-
gin females from the progeny in the proliferation step to be
the mating individuals for the next generation. Induced
dispersal was conducted between the line pairs at this stage
by exchanging the required number of non-virgin individ-
uals between lines according to the experimental dispersal
regime.
There were four replicates of each line pair at three
independent dispersal regimes: high dispersal, where two
individuals were transferred per generation (m = 0.04);
moderate dispersal, where one individual was transferred
every second generation (m = 0.01); and low dispersal
where one individual was transferred every eight genera-
tions (m = 0.0025). We maintained an equal sex ratio of
dispersers either by transferring a 1:1 sex ratio (high m) or
alternating the sex of the dispersing individuals at each
dispersal event (moderate and low m). We continued the
cultures by repeating this procedure until we had sampled
at three time points (Table 1). The first sample was taken at
the beginning of the experiment before the three dispersal
regimes had been implemented (T0) and then at two sub-
sequent points after the dispersal regimes had been
implemented (T1 and T2). The T1 and T2 sampling points
were calculated using the expected time for line pairs to
reach the half drift-dispersal equilibrium FST value,
because our definition of hybrid vigor assumes that the
lines have experienced independent evolution, which we
practically defined as significant genetic structure (FST).
Thus, sampling points T1 and T2 for different dispersal
rates are not comparable on a temporal scale, but are at the
same point of the drift-dispersal equilibrium trajectory.
Specifically, T1 was calculated as the expected time for
line pairs to reach the half drift-dispersal equilibrium FST
value, rounded up to the nearest whole number (Whitlock
1992; Eq. 1).
Fig. 2 Translocation experiment. Rank ordered mean Hij values of
the fitness component, net productivity, measured in recently isolated
Drosophila melanogaster lines. The line pairs axis designates which
two genetically differentiated lines are being assayed (Mean
FST = 0.0805 ± 0.01 SE; P = 0.001). Bars indicate bootstrap 95%
confidence interval. Asterisks (*) indicate significant deviation (P \0.05) from Hij = 0 after FDR correction for multiple tests
34 Conserv Genet (2011) 12:31–40
123
T1 ¼ lnð0:5Þln ð1� mÞ2 1� 1
2Ne
� �h i ð1Þ
where m is the dispersal rate and Ne is the effective pop-
ulation size (Table 1). T2 was calculated as 2 9 T1. We
confirmed that equilibrium had been attained by T2
through convergence of FST in line pairs starting from high
and low initial differentiation.
At each time point, we assessed hybrid performance (Hij
defined below) and we also compared the gross effects of
the dispersal regimes on net productivity by regressing the
number of adults produced from all the controlled crosses
in the habitat corridor experiment against the number of
generations that the line pairs had been exposed to a dis-
persal regime. Our hypotheses assumed that extensive
consanguineous mating was not occurring in our popula-
tions, thus we tested the veracity of this assumption at T0,
T1, T2 by conducting a Fisher’s Exact test for global
heterozygote deficiency in the seven autosomal microsat-
ellite loci, corrected for multiple tests using the FDR cor-
rection (Devlin et al. 2003).
Hybrid performance assay methods
We measured first generation (F1) Hij for net productivity,
estimated as the number of adult offspring observed a
specified number of days after a mating (Fig. S1 of the
supplementary information). Net productivity, which
comprises fecundity and survivorship, is a commonly
quantified fitness trait that can easily be monitored in both
laboratory and wild populations. We investigated Hij in the
F1 generation because both fitness increases and decreases
can be apparent in the F1 generation of crosses between
more inbred lines (Falconer and Mackay 1996; Edmands
1999). Our research did not specifically address fitness in
F2 and subsequent generations. To estimate Hij for net
productivity we performed F1 reciprocal crosses with
respect to sex between isolated lines as well as within-line
crosses (Fig. S1). To obtain mean net productivity esti-
mates all crosses were replicated at least 10 times. One-to-
six day old virgin flies of each sex were pooled and ran-
domly distributed among crosses. All crosses were per-
formed by mating five virgin males with five virgin females
(Ackermann et al. 2001). Mating was conducted for 3 days
after which the mating adults were removed. Cultures were
incubated for 16 days at 25�C to allow time for eclosion of
offspring (Fig. S1). To estimate Hij, the translocation
experiment required 12 replicates of 31 line-pair combi-
nations thus a minimum of 372 successful virgin crosses
(redundant within-line crosses were not conducted to
reduce workload). The hybrid performance assays for the
habitat corridor experiment were more extensive due to
temporal replication and required 10 replicates of 384 line-
pair combinations, thus a minimum of 3,840 successful
virgin crosses. Wherever possible, extra replicates of each
cross were carried out to compensate for occasional cross
failure and microbial contamination. The mean hybrid
performance statistic (Hij) for net productivity between
lines i and j was calculated as follows,
Hij ¼ logð�wij þ �wjiÞð�wii þ �wjjÞ
� �ð2Þ
where ð�wij þ �wjiÞ is the sum of mean net productivity
estimates of the reciprocal crosses between lines i and j,
and ð�wii þ �wjjÞ is the sum of mean net productivity
Table 1 Habitat corridor experiment
Dispersal regime Temporal sample
(generations)
Genetically differentiated line pairs Genetically similar line pairs
3_4 17_21 3_3 17_17
Mean Hij SE Mean Hij SE Mean Hij SE Mean Hij SE
High dispersal m = 0.04 T0 0 0.106 0.09 0.318 0.11 0.044 0.12 0.005 0.09
T1 6 0.302a 0.23 -0.010 0.07 0.201 0.14 0.160 0.06
T2 12 0.006 0.05 -0.046 0.03 -0.113 0.08 -0.054 0.04
Moderate dispersal m = 0.01 T0 0 0.106 0.09 0.318 0.11 0.044 0.12 0.005 0.09
T1 13 0.072 0.07 0.089 0.03 -0.048 0.06 -0.072 0.06
T2 26 -0.055 0.09 -0.003 0.08 0.064 0.05 -0.015 0.04
Low dispersal m = 0.0025 T0 0 0.106 0.09 0.318 0.11 0.044 0.12 0.005 0.09
T1 17 0.058 0.02 0.006 0.03 -0.028 0.06 0.055 0.05
T2 34 -0.119 0.11 0.022 0.15 -0.063 0.11 -0.155 0.30b
Mean Hij values at T0, T1 and T2 for all 24 different dispersal-line pair combinations, where the number of replicates (N) is four. Estimates of Hij
did not vary significantly from zero except for two line pair replicates of 17_17 that experienced low dispersala N = 3 instead of 4 due to an experimental errorb Two of the four replicates had a significant deviation (P \ 0.05) from Hij = 0 after FDR correction for multiple tests
Conserv Genet (2011) 12:31–40 35
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estimates of the within-line crosses. We used this ratio-
based hybrid performance statistic instead of calculating the
difference between F1 fitness and the parent mean (Dick-
erson 1969) because the difference method is dependent on
the magnitude of the fitness measure. However, a secondary
problem of ratios is the compression of hybrid breakdown
values into a range of 0–1, compared to a range of unity to
positive infinity for hybrid vigor. Therefore we log trans-
formed to ensure that hybrid breakdown had the same range
of values as hybrid vigor (zero to minus infinity or plus
infinity, respectively). The 95% confidence limits of Hij
were calculated using a bootstrap procedure, resampling
within each category of cross ( �wij, �wji, �wii and �wjj) using the
boot function within the boot package of R. The confidence
intervals were obtained from the appropriate quantile of the
bootstrap sample. See Supplementary Information for R
code. A line pair was considered to have significant Hij if
the interval did not include zero after correction for multiple
tests using the false discovery rate (FDR) correction (Devlin
et al. 2003).
Results
Experiment 1: Translocation
The experimentally imposed habitat fragmentation resulted
in significant levels of population structure among the iso-
lated laboratory lines (FST = 0.0805 ± 0.01 SE; P =
0.001). Unfortunately due to an irreconcilable labeling error
that occurred during a staff-changeover we are unable to
report pair-wise FST values for Experiment 1. We also note
that FST estimates in Experiment 1 were based on only six
microsatellite loci (England et al. 1996; Gunn 2003). Whilst
this relatively low number of loci may have resulted in low
power to detect genetic differentiation, we still observed
significant but low levels of genetic differentiation.
Following fragmentation we estimated mean net pro-
ductivity ( �wij, �wji, �wii and �wjj) of the 11 line pairs (387
crosses) and we observed that the variance in Drosophila
net productivity was inherently large, even when a large
number of replicates per cross type were conducted (10–12
minimum; Fig. 2). Despite low power resulting from the
inherently high variance in net productivity and after cor-
rection for multiple tests, two of the 11 line pairs exhibited
significant values of Hij, one instance was positive and the
other negative (Fig. 2). The other nine line pairs exhibited
a range of both positive and negative Hij values, however,
these did not differ significantly from zero. Thus, consis-
tent with our first hypothesis, significant Hij was detected in
18% of the translocation experiments. Consistent with our
second hypothesis, positive and negative Hij were both
detected among replicates of the source population.
Experiment 2: Habitat corridors
We designed the experiment such that there were two tra-
jectories towards equilibrium values of FST, by selecting two
initial levels of population differentiation. All FST values for
Experiment 2 are presented in Fig. S2 of the supplementary
information, but here we summarize this information. The
initially differentiated line pairs (T0 FST = 0.2 ± 0.01 SE;
P = 0.001) followed a downward trajectory towards equi-
librium values of FST that were lower than the initial T0 FST
(T2 high m FST = 0.03 ± 0.01 SE; T2 moderate m
FST = 0.12 ± 0.02 SE; T2 low m FST = 0.16 ± 0.03 SE).
In contrast, the initially undifferentiated line pairs (T0
FST = 0.01 ± 0.006 SE; P = 0.27) followed an upward
trajectory towards equilibrium values of FST that were higher
than the initial T0 FST (T2 high m FST = 0.06 ± 0.02 SE; T2
moderate m FST = 0.08 ± 0.01 SE; T2 low m FST = 0.16
± 0.03 SE). These FST estimates were based on seven
microsatellites (Holleley and Sherwin 2007) and thus may
have had slightly higher power to detect genetic differenti-
ation than Experiment 1 which utilized six microsatellites.
From a total of 3,930 controlled crosses, we estimated
the mean net productivity ( �wij, �wji, �wii and �wjj ) of the
replicated line pairs (3_4, 17_21, 3_3, 17_17) for each
dispersal regime (high, moderate, low) at three sampling
times (T0, T1, T2). Using the estimates of mean net pro-
ductivity we estimated Hij for replicates 1–4 of each line
pair (Fig. S2) and we present the grand mean Hij for each
line pair in Table 1. Full Hij information for all replicates is
provided in Fig. S2 of the supplementary information. At T0
no line pairs exhibited significant Hij. Over the course of the
habitat corridor experiment, populations with moderate to
high dispersal (1–4% per generation) did not develop sig-
nificant Hij (Table 1). However, two instances of significant
Hij were observed during the low dispersal regime (0.25%
per generation; Table 1; Fig. 3). At the sampling period T2,
line pair 17_17 displayed one instance of significant hybrid
vigor (H17_17 Rep 4 = 0.598) and one instance of significant
hybrid breakdown (H17_17 Rep 1 = - 0.823; Fig. 3). The
remaining two estimates of Hij for line pair 17_17 (repli-
cates 3 and 4) did not differ significantly from zero (Fig. 3).
Interestingly, the upward trajectory of line pair 17_17 at low
dispersal displayed the largest mean FST value of any line
pair at T1 (FST = 0.218 ± 0.08) or T2 (FST = 0.265 ±
0.07; Fig. 3). Line pairs 3_4, 17_21, and 3_3 did not display
any instances of significant Hij throughout the experiment
(Table 1). See Fig. S2 for FST values of all line pairs. Thus,
consistent with our first hypothesis, 12.5% of the line pairs
experiencing low dispersal displayed significant Hij at T2,
and consistent with our second hypothesis, we observed that
both hybrid vigor and breakdown can occur among repli-
cates of the same initial line pair after a period of inde-
pendent evolution (Fig. 3). Both hypotheses were rejected
36 Conserv Genet (2011) 12:31–40
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for all line pairs experiencing moderate and high dispersal,
as no significant hybrid vigor or breakdown was observed.
Overall there was very little evidence of heterozygote
deficiency in the experimental populations. Specifically, at
both T0 and T2 none of the populations showed a signifi-
cant heterozygote deficit. At T1 only two populations (Line
17Rep 1 at m = 0.01 and Line 4Rep 2 at m = 0.0025)
showed a significant heterozygote deficit after correction
for multiple tests, accounting for just 2.8% of populations
at the T1 sampling point and 1.2% over all populations. Net
productivity tended to increase over time and this increase
was positively correlated with dispersal rate (Fig. 4). Net
productivity in the high dispersal regime increased at a
faster rate than the moderate dispersal regime (Fig. 4).
Under the low dispersal regime net productivity did not
significantly increase or decrease over time (Fig. 4).
Discussion
We have demonstrated in two independent experiments that
it is possible for significant hybrid vigor and hybrid
breakdown to develop between lines of closely related
organisms, after short-term reproductive isolation (translo-
cation) or periods of restricted dispersal (corridors). Our
result challenges the commonly held notion that
populations maintained at a moderate size in isolation will
not exhibit hybrid vigor or hybrid breakdown when
recrossed. This effect is significant after correction for
multiple tests and despite low power resulting from inher-
ently high variation in Drosophila net productivity. Our
timescale is relatively short (60 generations in Experiment 1
and 12–34 generations in Experiment 2) thus relating to
times that might concern a manger of wild populations. We
encourage managers to consider, as we did, whether or not
the populations are likely to be in drift dispersal equilib-
rium, by using any available data on population size, dis-
persal rate and the time since alteration to these parameters.
We suggest that the occurrence of significant hybrid vigor
is not explained by a simple decrease in performance of the
partially isolated populations due to inbreeding depression
because the mean number of offspring in the corridor
experiment either increased or remained stable over the
course of the experiment (Fig. 4) and there was no excess of
consanguineous mating since no persistent heterozygote
deficiency was observed. Genetic causes of hybrid vigor are
a function of both dominance and epistatic effects but
without data from F2 or backcrosses, as is the case here, we
cannot separate these effects. The F1 hybrid breakdown
observed in our experiments is unlikely to be caused by the
disruption of co-adapted gene complexes, because divergent
local adaptation is unlikely to evolve in a mere 32–60 gen-
erations when there are no differences in environmental
conditions or population densities. Additionally, the dis-
ruption of co-adapted gene complexes is only expected to be
Fig. 3 Line pair 17_17 of the habitat corridor experiment. Mean Hij
values of the fitness component, net productivity, measured in line pair17_17 under low dispersal (m = 0.0025). Each line pair replicate
(N = 4) was maintained independently for the duration of the exper-
iment. The x-axis is the temporal sampling regime that was dependent
upon dispersal rate (Table 1). For the low dispersal rate (m = 0.0025),
T0 = generation zero, T1 = generation 17 and T2 = generation 34.
Bars indicate bootstrap 95% confidence interval. Asterisks (*) indicate
significant deviation (P\0.05) from Hij = 0 after FDR correction for
multiple tests. Estimates of genetic differentiation among line-pairs at
each sampling time are presented as mean FST values on the x-axis. See
supplementary Fig. S2 for graphs of complete Hij and FST dataset
Fig. 4 Habitat corridor experiment. Net productivity estimates result-
ing from controlled hybrid performance assays (N = 9.6 ± 0.25 SE)
in each of the imposed experimental dispersal regimes: a high
dispersal (4% per generation), b moderate dispersal (1% per gener-
ation) and c low dispersal (0.25% per generation). See Fig. S1 for
details of cross methodology
Conserv Genet (2011) 12:31–40 37
123
observed in the F2 or backcross generations, which were not
investigated in this study. Thus we suggest that the occur-
rence of both significant hybrid vigor and hybrid breakdown
in our experiments is most likely a result of population dif-
ferentiation in isolation due to genetic drift. Upon hybrid-
ization novel genetic interactions resulted in hybrid vigor
and hybrid breakdown. This explanation is corroborated
firstly by the development of significant population structure
in the translocation experiment and secondly in the habitat
corridor experiment by the observation that the line pair with
significant Hij (17_17; m = 0.0025) had the largest FST
value of any line pair in that experiment (Fig. 3 and Fig. S2).
Therefore we propose that genetic drift is the primary
mechanism affecting hybrid performance among moderately
sized populations.
Our second major observation was that in both of our
experiments, significant hybrid vigor occurred at the same
frequency as significant hybrid breakdown in the F1 gen-
eration. Interestingly this is quite different from results
typically found in animal and plant breeding, where the
crossbreeding of two lines usually has a positive effect on
the fitness of F1 offspring (Birchler et al. 2003; Oettler
et al. 2003; Ferreira and Amos 2006). This discrepancy is
most likely because the primary mechanism driving pop-
ulation differentiation in our experiment was genetic drift
affecting allele frequencies at polymorphic loci, whereas
most previous experiments have involved crosses between
more strongly inbred and/or selected lines which are likely
to have produced fixed or near fixed differences. A risk
averse manager, managing one or a few wild populations
should be aware that the risk of an undesirable outcome
during induced dispersal is not negligible.
Our third major observation drawn from the corridor
experiment, is the trend for populations with higher dis-
persal rates to experience greater net productivity (Fig. 4).
In our corridor experiment, dispersal is probably correlated
with net productivity because gene flow can counteract the
effects of genetic drift, augment genetic diversity and
maintain or increase the evolutionary potential of popula-
tions (Gandon et al. 1996; Swindell and Bouzat 2006). We
believe that alleviation of the effects of consanguineous
mating is not a likely explanation for this correlation
because we did not observe a higher frequency of signifi-
cant positive estimates of Hij relative to negative values of
Hij in these corridor experiments and saw no genetic evi-
dence for consanguineous mating (no persistent heterozy-
gote deficit). However, we cannot rule out the possibility
that the alleviation of very low levels of inbreeding
depression not detected by either our estimates of net
productivity or our estimates of heterozygosity could have
contributed to this correlation.
Our results are of great importance to conservation
efforts because we have demonstrated that both hybrid
vigor and hybrid breakdown can develop in moderately
sized but fragmented populations over timescales relevant
to conservation management and that these phenomena
appear to be equally likely to enhance or reduce population
viability in the short-term. Our experiment highlights that
simply managing populations to maximise their size is not
sufficient to ensure the success of an induced dispersal
management regime. The level of connectivity and the
period of isolation are critical factors affecting the fitness
of offspring resulting from an induced dispersal manage-
ment regime and thus the viability of the managed popu-
lations. Whilst our results suggest that managers’ ability to
utilize hybrid vigor as a tool to increase the short-term
viability of isolated populations may be limited, we suggest
that it is overcautious to completely prohibit all artificial
enhancement of dispersal between populations. We did not
reveal any evidence to suggest that hybrid vigor is more
likely than hybrid breakdown in the F1, however, a pre-
cautionary manager should definitely not view our results
as demonstrating that on average there was no preponder-
ance of hybrid vigor or breakdown and therefore feel it safe
to ignore both potential outcomes. Whilst both phenomena
occurred at a moderate to low frequency, they were still
detectable despite low power to detect Hij, due to inherent
variability of net productivity. A manager must therefore
be ready for both potential outcomes because the risk of an
undesirable outcome is not negligible. We note that
translocation practices are generally designed such that
there are restricted opportunities for hybridization by
introducing a small number of individuals are into a larger
population. Thus the size of the managed population will
determine what proportion of the population may be
affected by hybrid vigor and/or hybrid breakdown.
On the basis of our results we see the first priority of
population management to be the prevention of fragmen-
tation before it occurs. We acknowledge that preventing
fragmentation is not always possible and that often man-
agement is only initiated post-fragmentation or when the
population is in decline. Thus, our second recommendation
is to minimize the period of population isolation and pro-
mote connectivity between populations at a rate of C1%
dispersal per generation through mechanisms such as
habitat corridors or translocations. However, we note that
populations smaller than those investigated in this study
(\50 individuals) may require higher rates of dispersal to
counteract drift. This strategy employs the precautionary
principle by reducing genetic differentiation among popu-
lations and reducing the possibility of hybrid breakdown
occurring. Although such moderate to high dispersal rates
will also reduce the probability of hybrid vigor, we
observed a clear trend that dispersal rate is correlated with
net productivity, as have other authors for a wide range of
taxa (Spielman and Frankham 1992; Fischer and Matthies
38 Conserv Genet (2011) 12:31–40
123
1997; Sagvik et al. 2005). Further support for our recom-
mendation to maintain connectivity comes from studies
that have demonstrated that whilst hybrid breakdown can
occur initially when genetically differentiated populations
interbreed, this reduction in fitness is often temporary
(Templeton 2001). For the long-term survival of vulnerable
populations it is better to maintain high levels of selectable
variation via induced dispersal, despite the risk of short-
term negative fitness outcomes (Templeton et al. 2007).
Thus encouraging moderate rates of dispersal between
fragmented populations is the most conservative manage-
ment strategy overall from a genetic perspective.
Finally, we emphasize that there are many variables,
other than those discussed here, that need to be considered
before implementing induced dispersal as a management
practice, for example the transmission of disease (Hess
1994). Whilst the experiments carried out here cannot fully
measure all the potential effects of induced dispersal on the
viability of natural populations, our experiment provides
the first replicated base-line data about the frequency and
magnitude of hybrid vigor and hybrid breakdown in benign
laboratory conditions in a model organism. The frequency
and magnitude of hybrid vigor and hybrid breakdown may
be very different in other species, experiencing varied
selective pressures in the wild (Edmands 2006; Ferreira
and Amos 2006). However, our results provide empirical
data that can act as a starting point for further research,
such as replicated investigations of Hij in the F2 and sub-
sequent generations under varying levels of inbreeding,
which will help to better quantify the relative risks and
benefits of induced dispersal for conservation efforts.
Acknowledgments We acknowledge L. Tsai, E. Ho and J. Chao for
fly culture assistance; O. E. Gaggiotti, A. R. Templeton, J. L. Wang
and M. Mariette for comments on the manuscript and the Ramaciotti
Centre for Gene Function Analysis for DNA fragment size analysis.
This research was supported by Australian Research Council Grant
DP0559363 to WBS and RAN.
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