We studied the genetic structure of a hybrid zone between Red-legged (Alectoris rufa) and Rock (A. graeca) partridges in the southern French Alps using six allozyme loci. Allele frequencies showed sharp clinal variation across the hybrid zone, shifting by 60% over a distance of about 60 km, on average. Single-locus clines were coincident, but only partially concordant, with intermediate allele frequencies in the hybrid population. Percent polymorphic loci, heterozygosity, and linkage disequilibria were higher in the hybrids and in some populations near the hybrid zone than in allopatric populations. Nonrandom associations favored parental allele combinations. The hybrids and most of the allopatric populations were in Hardy-Weinberg equilibrium, but six populations near the hybrid zone showed a significant deficit of heterozygotes. The partridges in the hybrid zone included F 1 hybrids, backcrosses, and other recombinant genotypes. This hybrid zone could result from secondary contact of formerly allopatric populations following deglaciation of the Alps, probably not before 6,000 to 8,000 years ago. The width of the observed multilocus cline (70 to 160 km) is much shorter than expected (1,120 to 2,750 km) by neutral diffusion of allelic variants since the time of secondary contact of the two species (2,000 to 3,000 generations). Linkage disequilibria suggest that this hybrid zone is maintained by crossing of genetically divergent parentals and natural selection against hybrid genotypes. Although parapatric interspecific populations can exchange their genes through the hybrid zone, natural selection might constrain gene flow such that two species continue to evolve independently. Received 12 February 1998, accepted 23 July 1998.
Istituto Nazionale per la Fauna Selvatica, Via Cg Fornacetta 9, 1-40064 Ozzano dell'Emilia (BO), Italy; and
20ffice National de la Chasse, CNERA-Faune de Montagne, B.P. 38, F-06201 Nice Cedex 3, France
THE GENETIC STRUCTURE of inter- and intra-
specific hybrid zones is usually characterized
by abrupt and concordant clinal variation in al-
lele frequencies between the parental popula-
tions (Barton and Hewitt 1985, 1989; Harrison
1990, 1993; Hare and Avise 1996). Mosaic hy-
brid zones (Harrison 1986) can show complex
clines owing to differential habitat preferences
of the different hybrid genotypes (Rand and
Harrison 1989, Howard and Waring 1991, Sites
et al. 1995). Hybrid zones appear to be some-
what stable in time and space (Barton and
Hewitt 1985, 1989) and could be maintained by
dynamic equilibria between gene flow via dis-
persal and natural selection against hybrid ge-
notypes (Barton and Hewitt 1989). Alternative-
ly, transient hybridization, which results from
range expansion and recent contact between
reproductively compatible taxa, produces mov-
ing fronts of introgression that eventually lead
to local genetic extinction of the introgressed
populations (Gill 1994, 1997). Hybrids can be
intrinsically unfit and then eliminated by selec-
E-mail: met0217@iperbole.bologna.it
tion due to endogenous factors ("tension
zones"; Key 1968, Barton and Hewitt 1985,
1989; Searle 1993, Sites et al. 1995). Alterna-
tively or concomitantly, hybrid genotypes can
be exposed to exogenous selection pressures in
different habitats ("clinal" models; May et al.
1975, Endler 1977) and occasionally can be
more fit than parentals at particular transition-
al locales ("bounded hybrid superiority" mod-
el; Moore 1987, Arnold and Hodges 1995,
Emms and Arnold 1997).
Hybridization is relatively common in birds
(Grant and Grant 1992), and many avian par-
apatric distributions have been described (e.g.
Prigogine 1980, Rising 1983) that apparently
represent stable zones of overlap and hybrid-
ization (sensu Short 1969). Hybridizing avian
populations often show low geographic varia-
tion and absence of diagnostic alleles at both
nuclear and mitochondrial loci (Barrowclough
1980, Brown and Robbins 1986, Grudzien and
Moore 1987, Corbin and Wilkie 1988, Moore et
al. 1991, Saino et al. 1992). Morphological traits
usually have sharper clinal transitions, which
could be controlled by natural and sexual se-
lection (Moore 1987, Gill 1997). Some avian hy-
brid zones appear to be stable (Moore and
Buchanan 1985), whereas others are transient
(Gill 1997) or have shifted their geographic po-
sition during historic times (Cook 1975, Rising
1983).
The Red-legged Partridge (Alectoris rufa; dis-
tributed from Iberia to France and northwest-
ern Italy) and Rock Partridge (A. graeca; dis-
tributed throughout the Alps, central and
southern Apennines and Sicily in Italy, and the
Balkans, reaching Albania and Greece; Johns-
gard 1988) are largely allopatric but hybridize
along the border of the southern French Alps
(Bernard-Laurent 1984; Fig. 1). As a conse-
quence of climate deterioration at the Pliocene/
Pleistocene boundary, the Red-legged and
Rock partridges diverged probably in western
and eastern refugia, respectively, and then ex-
panded during the Holocene postglacial warm-
ing to a secondary contact zone (Randi et al.
1992, Randi 1996). These two species are ge-
netically well differentiated and probably are
sister taxa (Randi 1996). They have diagnostic
plumages that allow identification of pure and
hybrid birds (Table 1). The morphologically hy-
brid population presently is distributed over a
band of open habitat, about 15 km wide, at
moderate elevations along the southern edge of
the French Alps (Bernard-Laurent 1984; Fig. 1).
In the past, however, the hybrid zone was prob-
ably wider, ranging from the northern French
Alps to the western Apennines and the Ligur-
ian Alps in Italy (Degland and Gerbe 1867,
Spantb 1979).
To date, the genetics of this partridge hybrid
zone has not been studied. Here, we report on
the genetic structure of the hybrid population
relative to Red-legged Partridge and Rock Par-
tridge populations close to and far from the hy-
brid zone. Results of a survey of six enzyme loci
are used to describe single- and multilocus al-
lelic clines and introgression across the hybrid
zone, as well as patterns of allele diversity and
linkage relationships between loci. Genetic re-
sults are integrated with palaeoclimatic, eco-
logical, and behavioral data to suggest the pos-
sible origin and dynamics of this hybrid zone.
MATERIALS AND METHODS
During the 1989 to 1993 hunting seasons, we col-
lected 95 Red-legged Partridges and 320 Rock Par-
tridges (hereafter called the "allopatric popula-
tions") near or far from their contact zone (Fig. 1).
Fourteen allopatric populations were sampled from
the southern French and Italian Alps to the eastern
Alps. Four other allopatric populations were sam-
pled outside the Alps: two western Red-legged Par-
tridge populations from Portugal and Spain, and two
eastern Rock Partridge populations from central Ap-
ennines (Italy) and Albania. We collected 38 par-
tridges within the area of species' contact and over-
lap (the "hybrid zone" across the southern French
Alps). The plumage patterns of these birds were an-
alyzed using the criteria of Bernard-Laurent (1984);
30 of the birds were morphological hybrids that ex-
hibited various combinations of species-specific
plumage traits (population no. 4; the "hybrid popu-
lation;" see Fig. 1, Table 2), 7 had typical Rock Par-
tridge plumage (population no. 5; "Rock Partridges
within the hybrid zone"), and 1 was a pure Red-leg-
ged Partridge (excluded from the following genetic
analyses). All birds collected outside the hybrid zone
exhibited morphological traits of pure Red-legged or
Rock partridges, depending on sampling locations.
Liver and heart tissue samples were collected and
stored frozen at -80C. About 0.5 g of each tissue
sample was separately homogenized in 1-mL 0.01 M
Tris/HC1 pH 7.5, 1 mM Na 2 EDTA, and 1 mM [3-mer-
captoethanol buffer and centrifuged for 15 min at
17,000 rpm at 4 C. Clear supernatants, diluted in 1
volume of 40% glycerol, were aliquoted in microtiter
plates. Polyacrylamide gel electrophoresis was used
to study allelic variability of the following six loci,
which had high intrapopulation polymorphism and
differed in allele frequencies between the two species
of partridges (Randi et al. 1992): (1) liver ct-naphthyl-
acetate esterase-2 (Est; E.C. No. 3.1.1.1); (2) cytoplas-
mic glutamate-oxaloacetate transaminase (Got; E.C.
No. 2.6.1.1); (3) cytoplasmic malic enzyme (Me; E.C.
No. 1.1.1.40); (4) cytoplasmic isocitrate dehydroge-
nase (Idh; E.C. No. 1.1.1.42); (5) mannose phosphate
isomerase (Mpi; E.C. No. 5.3.1.8); and (6) amylase
(Amy; E.C. No. 3.2.1.1). Electrophoretic conditions
are given in Randi et al. (1992). Electromorphs were
treated as alleles and coded by their mobility from
the origin, with the most anodal allele named "A,"
and so forth.
Because intrapopulation allele frequencies did not
fluctuate significantly among sampling years (Work-
man and Niswander's contingency test; data not
shown), we pooled all samples collected at the same
locality in different years. The electrophoretic data
were analyzed using the following software and sta-
tistical methods: (1) BIOSYS-1 (Swofford and Selan-
der, 1989) was used to compute allele frequencies,
gene-diversity estimates (P = percent polymorphic
loci; A = mean number of alleles per locus; Ho and
H c = observed and Hardy-Weinberg expected het-
erozygosity). We used single-locus chi-square tests
of Hardy-Weinberg equilibrium (HWE) with Le-
vene's correction for small sample size and Fisher's
9
10
12
11 13 14 15
16
100 Km
FIG. 1. Distribution of Red-legged Partridges (striped areas) and Rock Partridges (dotted areas) in France and
Italy, and distribution of sampled populations. The darker area overlapping part of the Rock Partridge distribution
in northwestern Italy indicates the distribution of recently extinct Rock Partridge populations in the western Italian
Apennines. The reticulated area indicates the distribution of recently extinct Red-legged Partridge populations in
Piedmont (Italy). The present hybrid zone is indicated by an oval. The sampled populations are numbered as
follows (numbers 1 to 3 are Red-legged Partridges; numbers 5 to 18 are Rock Partridges): 1 = central Portugal; 2
= central Spain; 3 = Cipieres, France (ca. 20 to 24 km from the hybrid zone); 4 = hybrids from the hybrid zone;
5 = Rock Partridges from the hybrid zone; 6 = the high Valley of Tin6e, France (14 to 28 km from the contact
zone); 7 = Cuneo, Italy (30 to 40 km from the contact zone); 8 = Champsaur, France (70 to 80 km); 9 = Queyras,
France (75 to 85); 10 = Isere, France (80 to 90 km); 11 = Valle d'Aosta, Italy (130 to 150 km); 12 = Savoie, France
(170 to 190 km); 13 = Novara, Italy (ca. 250 km); 14 = Sondrio, Italy (ca. 350 km); 15 = Brescia, Italy (ca. 400 km);
16 = Pordenone, Italy (ca. 550 km); 17 = central Apennines, Abruzzo, Italy; 18 = Albania. The pie diagrams
indicate the percent of Red-legged Partridge (white) and Rock Partridge alleles (black) found in each population.
TABLE 1. Plumage differences between Rock Partridge and Red-legged Partridge.
327
Character Rock Partridge Red-legged Partridge
Head color
Bar coverts
Black eye stripe
White line over eye
Frontal black band
White throat patch
Black necklace
Nape
Flank feathers
Axillary feathers
Gray
Black with buff tips
More than 2 mm wide
Narrow (1 mm wide)
>2 mm wide
Maximum height >5 cm
Sharply demarcated
No streak on nape
Two black bars
At least one black bar
Forehead gray, rest of head brown
Yellow-buff
Very narrow (<1 mm)
Line on forehead broadens into eye stripe
Very narrow (<1 mm) or incomplete
Smaller (maximum height <5 cm)
Spreads into black streaks on upper chest
Some black streaks on nape
One black bar
No black bar
exact probability test (Weir 1990). Workman and Nis-
wander's (1970) contingency chi-square test was
used to assess the significance of allelic heterogene-
ity among samples. We computed various genetic-
distance matrices (D) and used Rogers' D (1972) to
obtain UPGMA (Sneath and Sokal 1973) and neigh-
bor-joining dendrograms (NJ; Saitou and Nei 1987).
(2) FSTAT and LINKDIS (Black and Krafsur 1985a, b)
were used to compute F-statistics (Wright 1965) and
to calculate pairwise linkage disequilibrium coeffi-
cients within each population estimated as R, the
standardized correlation between allele associations.
(3) Genetic relationships among populations were
represented also through multivariate analyses.
NTSYS-pc (Rohlf 1990) was used to obtain the min-
imum spanning tree (MST) and non-metric multi-
dimensional scaling (MDS) of a principal coordinate
analysis (Gower 1966) of the Rogers' D matrix.
RESULTS
Genetic variability of populations.--Allele fre-
quencies (Table 2) diverged significantly be-
tween allopatric populations of Red-legged
and Rock partridges at Est, Mpi, Got, and Me
(Workman and Niswander's contingency test)
but not at Amy or Idh. Only one allele, Got-C,
was totally absent from one species (Red-leg-
ged Partridge) and highly frequent (0.81) in
the other (Rock Partridge) and in hybrid pop-
ulation 4. Some alleles occurred at low frequen-
cy in one species and were found in hybrid
population 4 and in populations sampled
around the hybrid zone. Est-C, Mpi-B, and Idh-
B were absent in the Iberian Red-legged Par-
tridge (populations 1 and 2) but frequent in all
Rock Partridge populations and present in the
hybrid population 4 and in the French Red-leg-
ged Partridge (population 3). Got-A, a Red-leg-
ged Partridge allele, was present in hybrid pop-
ulation 4, in Rock Partridges within the hybrid
zone, and in allopatric populations 6, 9, and 10
near the hybrid zone. Amy-C was present at
low frequency in Rock Partridge allopatric
populations 6 and 8 and in hybrid population
4. Estimates of gene diversity increased toward
the hybrid zone, the mean number of alleles per
locus (A) was 2.0, P (0.05 criterion) 50%, Ho
0.19 in all the populations sampled around
the hybrid zone (3 to 10; see Fig. 1), and the
highest values of H o and H,. occurred in hybrid
population 4. Heterozygosity was higher in
French and Italian Rock Partridges sampled
near the hybrid zone than in other allopatric
Italian and Iberian populations. These findings
suggest introgression of alleles through the hy-
brid zone.
Significant deviations from HWE (Table 3)
were observed for some of the loci in six pop-
ulations near the hybrid zone, and in Red-leg-
ged Partridges from Portugal. These birds were
collected at four localities (Bombarral, Mertola,
Campo Major, Castro Marlin) in central and
southern Portugal and may represent a hetero-
geneous sample with different allele frequen-
cies at the different locales (i.e. the Wahlund ef-
fect; Hartl and Clark 1990). Nevertheless, they
were pooled in a single group because differ-
ences in allele frequencies among them have no
effects on the description of the genetic clines.
Hybrid population 4 was in HWE. All Rock
Partridge populations far from the hybrid zone,
i.e. east of the Savoie/Valle d'Aosta Alps (pop-
ulations 13 to 18; see Fig. 1) were in HWE. Sig-
nificant values of the fixation index F were al-
ways due to a deficit of heterozygotes from ex-
pected (i.e. positive F values; Table 3).
The genotypic composition of hybrid and al-
lopatric populations was described through the
distribution of an individual hybrid index (Bar-
ton and Gale 1993):
328 RANDI AND BERNARD-LAURENT [Auk, Vol. 116
¸¸
¸¸
TABLE 3. Loci showing significant (P < 0.05) devi-
ations from Hardy-Weinberg equilibrium and
probability values obtained using Levene and
Fisher chi-square tests. F is the fixation index
(Wright 1965).
Locus Levene test Fisher test F
Red-legged Partridge-1 (n = 20)
Est 0.003 0.030 0.608
Amy 0.000 0.001 0.762
Red-legged Partridge-3 (n --- 63)
Me 0.012 0.017 0.312
Rock Partridge-5 (n = 7)
Mpi 0.001 0.091 1.000
Got 0.004 ns 0.600
Rock Partridge-6 (n = 72)
Me 0.021 ns 0.264
Rock Partridge-7 (n = 53)
Idh 0.005 0.017 0.369
Rock Partridge-9 (n = 28)
Est 0.020 0.010 0.407
Got 0.000 ns 0.486
Rock Partridge-1 (n = 8)
Mpi 0.038 ns 0.590
z = az,, (1)
where a = 1/2n, n = the number of diagnostic
marker genes, and z, = genotypes generated by
the marker genes (indicated as 0, 1, or 2). The
individual hybrid index was computed using
the frequencies of the most common alleles in
the Red-legged Partridge populations (and in
the case of loci with three alleles, i.e. the fre-
quency of Est-A and not Est-B+C, and so
forth); therefore, values of z can range from 0
(for genetically pure Rock Partridges) to 1 (for
pure Red-legged Partridges). Allopatric popu-
lations of Rock Partridges (Fig. 2A) and Red-
legged Partridges (Fig. 2C) had very skewed
distributions of z, with modal values of 0 and
0.9, respectively. The distribution of z within
hybrid population 4 (Fig. 2B) was not unimodal
and therefore did not indicate a predominance
of F1 hybrids (the central class with 50% genes
derived from both the parents). Nor was it
strictly bimodal (indicating the complete ab-
sence of F individuals), but there were fre-
quent backcrosses (25% and 75% classes) and
other recombinants. French Red-legged Par-
tridges and Rock Partridges collected near the
hybrid zone (not shown) had a high frequency
of intermediate genotypes, which suggests al-
lelic introgression. These findings are consis-
tent with the mixed-phenotype composition of
the partridges sampled within the hybrid zone:
hybrid, Rock Partridge, and Red-legged Par-
tridge phenotypes accounted for 86%, 10%, and
4%, respectively, of the studied partridges (Ber-
nard-Laurent 1984). Outside the hybrid zone
all birds appeared to be phenotypically pure.
Multivariate relationships among populations.-
Populations were plotted in a 3-dimensional
space (MDS), and a minimum-spanning tree
(MST) was superimposed to show relation-
ships among the populations (Fig. 3). Allopat-
eo A eo C
3o
20 2 20
B
,I.ll ,I
Z values (x 100)
FIG. 2. Distribution of the frequency (%) of the individual hybrid index based on allozyme frequencies (z
x 100) in: (A) eastern Rock Partridges (populations 13 to 18); (B) populations 4 and 5 sampled in the hybrid
zone; and (C) western Red-legged Partridges (populations 1 and 2). Intermediate values of z indicate F ge-
notypes, whereas extreme values (<25, >75) indicate different backcrosses and recombinant genotypes.
rridge populations
F!G. 3. Three-dimensional distribution of partridge populations obtained by non-metric multidimension-
al scaling of a principal coordinate analysis (Gower 1966) of the Rogers' D matrix. Populations are connected
by a minimum spanning tree. See Figure 1 for acronyms and distributions of populations.
ric Red-legged and Rock partridge populations
were completely separated on opposite sides of
the first dimension, and the hybrid population
was almost intermediate. The tight cluster of
Rock Partridges on the right side of the plot en-
compasses all populations east of Valle d'Aosta
and the Savoie Alps (populations 13 to 18) and
indicates low levels of genetic divergence
among populations. On the contrary, the west-
ern Rock Partridge populations (numbers 5 to
12) exhibited increased genetic divergence.
MDS also depicted the introgression of Red-
legged Partridge alleles into the Rock Partridge
populations near the hybrid zone (i.e. popula-
tions 5 to 7, which were collected near the hy-
brid zone, were directly linked to hybrid pop-
ulation 4 through the MST; see Figs. 1 and 3).
Dendrograms obtained by clustering Rogers' D
matrix with UPGMA and NJ procedures were
very similar (not shown) and confirmed the re-
lationships obtained with MDS.
Genetic clines.--Single-locus clines at the four
loci that showed significant interspecific diver-
gence (Est, Mpi, Got, Me) were represented by
plotting frequencies of the most frequent alleles
in the Red-legged Partridge populations
against distance of each population from the
center of the hybrid zone. Genetic clines
showed similar shapes and were roughly co-
incident, with intermediate and abrupt change
of allele frequencies in hybrid population 4. Al-
though frequencies of Got-B and Me-B decayed
with exponential regularity far from the hybrid
zone, the Est-A and Mpi-A alleles showed
greater local departures from the curve. In par-
ticular, Rock Partridges from Valle d'Aosta and
Savoie (populations 11 and 12) exhibited in-
creased frequencies of Est-A (Fig. 4A). Other
populations deviated from a regular clinal pat-
tern, e.g. population 10 had high frequencies of
Mpi-A and Got-B (Figs. 4B, 4C), and popula-
tion 7 had a high frequency of Me-B (Fig. 4D).
Pairwise comparisons of allele frequencies in
populations 4 to 18 showed that Est and Mpi
alleles introgressed into Rock Partridges sig-
nificantly more than Me and Got alleles, and
Mpi significantly more than Me and Got alleles
(Fisher's exact test at each locality with sequen-
tial Bonferroni adjustment; Rice 1989). These
allelic fluctuations suggest differential intro-
gression of Red-legged Partridge alleles into
some Rock Partridge populations, although the
observed allelic fluctuations could be due to
low sample size (i.e. population 7; n = 8), or to
local isolation and random drift (i.e. population
10).
We computed the hybrid index: HI = Z(Pl)/
4 (Vanlerberghe et al. 1988) using the most fre-
quent allele (p) in Red-legged Partridges at
each of the four discriminating loci (Est-A,
100 --
80
6O
40-
20--
41
6
5 - 7
8-1(
I
-1000 -500
Est-A I 2
8O
I 11 I
19i 3 60
40
6-8
15 16 17 18 I
500 lOOO -lOOO -500
(B)
Mpi-A
500 1000
6O
40
20-
4
6-9
7-8
I
-600
(c)
Got-B
10
1112 16 17 18
I
500 1000
100
80
60
40
I I
(o)
Me-B
-1000 -600 0 500 1000
80-
(E)
Hybrid index
I
-1000 -500
m 600 1000
FIG. 4. Clinal variation of four diagnostic alleles in Red-legged Partridge, Rock Partridge, and hybrid
populations. Allele frequencies (x100) are plotted against distance (km) of each population from the mor-
phological hybrid zone (0 km). Populations are plotted from east to west, according to the map in Figure 1.
The loci are: (A) Est-A, (B) Mpi-A, (C), Got-B, and (D) Me-B; (E) is the plot of the hybrid index computed
following Varlenberghe et al. (1988). Distances between populations are approximate measures from the map.
Mpi-A, Got-B, Me-B). Values of HI plotted
against distance from hybrid population 4 (Fig.
4E) exhibited a stepped clinal transition from
the high frequencies of Red-legged Partridge
alleles to the eastern Rock Partridge samples.
Hybrid population 4 had HI = 0.53, almost ex-
actly intermediate between the HI of Red-leg-
ged Partridges far from the hybrid zone (0.98
in Spain and 0.90 in Portugal) and that of east-
ern Rock Partridges (0.03 in Albania). The
width of the multilocus cline estimated by fit-
ting the observed sigmoid plot to a logistic re-
gression model was w = 70 to 80 km, whereas
it was w = 140 to 160 km when estimated as the
distance between HI = 0.78 and 0.22 (corre-
sponding to the difference between 0.80 and
0.20, as corrected following May et al. 1975).
Cline width indicates that introgression of
Red-legged Partridge alleles into Rock Par-
tridge populations extends far from the geo-
graphic location of the hybrid zone, which is
only 15 km wide as assessed through the dis-
tribution of hybrid phenotypes. These values of
HI in fact included some of the populations
sampled west of the Savoie/Valle d'Aosta Alps
(i.e. populations 6, 7, and 10; Figs. 1 and 4E).
Red-legged Partridge and other Rock Partridge
populations in France (i.e. 8, 9, 11, and 12) had
HI values very close to 0.78 and 0.22, respec-
tively. Therefore, the allozyme cline included
some phenotypically pure Rock Partridges as
follows: population 6 (collected at ca. 14 to 28
km from the hybrid zone), 7 (collected in Pied-
mont, Italy, from the eastern slopes of the
Southern Alps, ca. 30 to 40 km from the hybrid
zone), 10 (collected in Isere, ca. 80 to 90 km
from the hybrid zone), and 12 (collected in Sa-
voie, ca. 170 to 190 km from the hybrid zone;
see Fig. 1). Introgression of Red-legged Par-
tridge alleles into Rock Partridge populations
located within 100 km of the center of the hy-
brid zone (i.e. populations 6, 7, 8, and 10) in-
volved all polymorphic loci, whereas high HI
values of the Savoie (12) and Valle d'Aosta (11)
populations were due to the high frequency of
Est-A alone (Fig. 4A). The allozyme cline was
not defined on the Red-legged Partridge side.
It was not possible to sample more French Red-
legged Partridge populations because the birds
are rare toward the hybrid zone, and some-
times populations are heavily restocked with
captive-raised birds.
Linkage disequilibrium.--Analysis of linkage
disequilibrium revealed significant R coeffi-
cients in five of 18 populations (Table 4) owing
to nonrandom positive associations among al-
leles derived from the same parental popula-
tion. Average pairwise R values (Table 2) were
plotted against distances from the hybrid zone
(Fig. 5A) and compared with the plot of the ob-
served heterozygosities (Fig. 5B). Spacial
trends in both estimates corresponded with
multilocus and single-locus clines: maximum R
and Ho values were in or near the hybrid zone.
Two Rock Partridge populations (7 and 10)
within the area of introgression had R values
higher than the hybrids (Fig. 5A). We cannot
TABLE 4. Loci with significant (P < 0.05) values of
pairwise linkage disequilibrium. Alleles of each
pair are both indicated in capital letters if conspe-
cific (e.g. row 1, Got-B and Me-B ar highly frequent
alleles in Red-legged Partridges), or one in capital
and one in lowercase if heterospecific (row 2, Got-
B is a Red-legged Partridge allele, and Me-a is a
Rock Partridge allele). Observed = the observed
frequency (%) of a given allele association; Ex-
pected = expected random frequency (%) of a giv-
en allele association; P = probability of occurrence
of deviations between observed and random ex-
pected allele associations.
Loci Alleles Observed Expected P
Red-legged Partridge-3 (n = 63)
Got / Me B / B 73.5 70.4 0.02
B/a 29.5 32.6 0.02
Hybrids (n = 30)
Est/Got
Got/Me
A/B 17.5 14.7 0.04
A/c 19.0 22.7 0.01
C/b 4.5 7.3 0.04
C/C 15.0 11.0 0.01
B/a 8.5 13.2 0.00
B/B 13.5 8.8 0.00
C/A 24.0 20.4 0.02
C/b 10.0 13.6 0.02
Rock Partridge-5 (n = 7)
Est/Me A/A 5.5 4.5 0.02
A/B 2.5 1.5 0.02
C/A 6.5 5.5 0.02
C/b 0.5 1.5 0.02
Rock Partridge-7 (n = 53)
Mpi/Got A/B 1.0 0.2 0.00
B/b 0.0 0.8 0.00
Rock Partridge-9 (n = 28)
EST/Mpi C/a 10.0 13.5 0.04
C / B 26.0 22.5 0.04
B/A 2.0 0.7 0.01
B/b 0.0 1.2 0.01
rule out an effect of small sample size on esti-
mated R at Cuneo (population 7; n = 8), but the
Isere sample (population 10; n = 28) was larger
than the average sample size of this study (n =
25).
DISCUSSION
The Alps represent a barrier to dispersal and
an area of secondary contact among many
southwestern and southeastern taxa (Taberlet
et al. 1998). The slopes of the southern French
Alps near the Italian border support several
hybrid zones, including those formed by two
chromosomal races of a grasshopper (Podisma
pedestris; Hewitt 1975), two subspecies of crow
35
3O-
25-
2O
Km
35O B 4
300 6 7
250 8
150 12 16
10(] i 2 18
Km
FIC. 5. Plots of the (A) average coefficient of linkage disequilibrium R (x100), and (B) observed hetero-
zygosity (x100) across the partridge hybrid zone.
(Corvus corone; Saino et al. 1992), and the two
species of partridge described in this paper.
The Alps were covered by ice during the last
glacial maximum, about 18,000 to 20,000 years
ago, and most subalpine areas and the central
European plains consisted of tundra (Roberts
1989). Alpine and subalpine habitats were not
suitable for partridges, which typically inhabit
arid flatlands, open hilly slopes, and rocky de-
forested mountains. Following Holocene warm-
ing about 10,000 years ago, ice and tundra re-
treated, and many plant and animal popula-
tions expanded their ranges northward from
southern refugia (Hewitt 1989).
Biochemical and molecular analyses (Randi
et al. 1992, Randi 1996) suggested that Red-leg-
ged and Rock partridges speciated in allopatry
about 1.5 to 2.0 millions years ago, at the onset
of Pliocene/Pleistocene climatic deterioration.
Red-legged and Rock partridges probably
were confined to meridional refuge areas in
Iberia, Italy, France, and the Balkans, at least
until 8,000 to 9,000 years ago, when most of Eu-
rope and the Alps were covered by forests. Pa-
laeoecology of the Alps suggests that deforest-
ed areas resulting from climatic changes and
human activities were widespread from 6,000
to 5,000 years before present (Hewitt 1993). The
spread of prehistoric agriculture may have fa-
vored the dispersal of partridges that often use
pastures, vineyards, orchards, and other culti-
vated lands (Johnsgard 1988). Thus, the present
Red-legged Partridge x Rock Partridge hybrid
zone probably originated from a secondary
contact in the southern French Alps following
the Holocene climatic amelioration, not before
8,000 years ago and probably about 6,000 years
ago.
Steep variation in allele frequencies was cen-
tered at hybrid population 4, with a shift of val-
ues of the multilocus hybrid index HI by 60%
over about 60 km distance. Allozyme clines
across the partridge hybrid zone were coinci-
dent but only roughly concordant, because al-
lele frequencies at some loci fluctuate in popu-
lations sampled within about 160 km of the hy-
brid zone (Fig. 4). The hybrid population had
higher heterozygosity and linkage disequilib-
ria than other populations within and near the
hybrid zone. Coincident and concordant clines
generated by different and non-linked struc-
tural loci, as well as linkage disequilibria, are
predicted by the tension-zone model of hybrid
zones (Barton and Hewitt 1985). The observed
allozyme clines in partridges could be main-
tained through a balance between selection
against hybrid genotypes and migration of pa-
rental and recombinant individuals. However,
the multimodal distribution of the individual
hybrid index z (Fig. 2), due to the presence of
different genotypic classes within the hybrid
population, suggests that intrinsic selection
against F hybrids within the hybrid zone is
weak. Moreover, although the hybrid popula-
tion was in Hardy-Weinberg equilibrium, other
populations near the hybrid zone showed a sig-
nificant deficit of heterozygotes and linkage
disequilibrium, suggesting that natural selec-
tion could eliminate some hybrid genotypes
and impede gene flow outside the phenotypic
hybrid zone.
Variations in the observed shape of the allo-
zyme clines could be due to stochastic fluctu-
ations (e.g. small size of local populations or
small sample size) or to selective barriers
against gene flow (Barton and Hewitt 1985,
Szymura and Barton 1986, Pialek and Barton
1997). The expected width of a cline, as derived
from neutral diffusion of allelic variants, is w =
2.51T 0.5 (Barton and Gale 1993), where is the
gene flow computed as the standard deviation
of juvenile dispersal, and T is the presumed
time in generations since the secondary con-
tact. The observed allozyme cline in partridges
has a width of w = 70 to 160 km (Fig. 4E). It is
difficult to obtain an estimate of , because em-
pirical observations are scarce. From Bernard-
Laurent's (1991a) observations on movements
of 13 radio-tagged juvenile hybrid partridges,
short-term dispersal was = 1.0 km, with
highly variable individual ranges (0.3 to 25
km). Maximum reported travel distances for
Rock Partridges are 25 km in France (Bernard-
Laurent, 1991b) and 8 to 9 km in Austria (Haf-
ner 1994). Using values of dispersal of 10 to 20
km per generation, and w = 70 to 160 km, we
computed values of T = 5 to 40 generations,
corresponding to 10 to 120 years if generation
time is 2 to 3 years, that are necessary to pro-
duce the observed genetic cline, assuming strict
neutrality. Accordingly, the observed multilo-
cus cline should be very recent, and / or the dis-
persal rate very low, if generated by neutral dif-
fusion of alldes. In other words, neutral dif-
fusion with ranging from 10 to 20 km per
generation and T of 2 to 3,000 generations since
the secondary contact of the two species should
have produced a cline of 1,120 to 2,750 km,
which is substantially wider than the observed
cline of 70 to 160 km. The theory of tension
zones offers more rigorous and formal ap-
proaches to the study of genetic clines (Szy-
mura and Barton 1986, Mallet et al. 1990, Pialek
and Barton 1997), but the incompleteness of our
data prevent further elaboration. In particular,
we have not sampled more Red-legged Par-
tridges in France because they are scarce
around the contact zone, and most localities
have been heavily restocked with captive-
raised birds. Therefore, because only one side
of the hybrid zone was properly sampled, the
position, shape, and width of the cline cannot
be estimated with greater precision.
In documenting autumn migratory move-
ments of Rock Partridges, Bernard-Laurent
(1991b) found that birds were able to fly across
the hybrid zone and reach the Red-legged Par-
tridge habitat at lower elevations. Migratory
behavior and dispersal suggest a model of for-
mation and dynamics of the partridge hybrid
zone: parapatric populations of partridges are
separated by boundaries that are located along
an area of equilibrium between a cline of de-
creasing adaptability to environmental condi-
tions (for Red-legged Partridges at higher ele-
vations) and a cline of increasing interspecific
competition (for Rock Partridges at lower ele-
vations in the habitat of the other species). This
boundary can be crossed, for example, by Rock
Partridges that penetrate the Red-legged Par-
tridge areas where they occasionally stay and
breed with the resident Red-legged Partridges.
The fertility of hybrids has been directly as-
sessed after capturing 13 fertile pairs with hy-
brid phenotypes (Bernard-Laurent 1990). The
multimodal distribution of z suggests that fer-
tile F hybrids can initiate a hybrid population
that can backcross and introgress into border-
ing populations. The stability of the hybrid
zone is sustained by the high reproductive suc-
cess of hybrids (Bernard-Laurent 1987), but the
diffusion of hybrids outside the narrow hybrid
zone toward the Rock Partridge habitat could
be limited by higher winter mortality owing to
starvation caused by deep snow (Bernard-Lau-
rent 1988).
Red-legged Partridges and Rock Partridges
are widespread, and their distributions are
fragmented in patches of allopatric and para-
patric populations that are more or less genet-
ically isolated through reduced gene flow
among them. The homogenizing effects of in-
trogression through the hybrid zone seem to be
strongly counteracted by natural selection
against recombinant genomes, which forces the
hybrid zone to remain narrow at the present lo-
cation and acts as a strong barrier to gene flow
of Red-legged Partridge alleles into Rock Par-
tridge populations.
ACKNOWLEDGMENTS
We thank P. Leonard, D. Dias, I. Artuso, M. Pagan-
in, and D. Febbo for help in collecting partridges. P.
U. Alkon, A. J. Baker, N. Barton, P. Boursot, E Van-
lerberghe, and an anonymous referee provided sug-
gestions that greatly improved an earlier version of
the manuscript. Laboratory assistance of A. L. Bolelli
and V. Lucchini has been deeply appreciated. This
study was supported by the Istituto Nazionale per la
Fauna Selvatica Ozzano dell'Emilia (BO), Italy, and
Office Nationale de la Chasse, France.
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