Ecologia Mediterranea
Ecologia Mediterranea
Ecologia Mediterranea
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CATERINA MAGRINI, MICHELE CENTO, EMILIANO MANZO, MASSIMO PIERPAOLI, LIVIA ZAPPONI, ROBERTO COZZOLINO<br />
26<br />
equilibrium were found in sampled population<br />
(p≥0.05).<br />
From all captured weasels, only one pair<br />
(1,09%) from the total possible pair wise<br />
comparisons (91) showed close genetic kinship:<br />
the animals F2-M5 were certainly constituted<br />
by parent/offspring (r=0.4; R=0;<br />
p ≤0.001). For all others simulated comparisons<br />
made by KINGROUP program, r values<br />
(relatedness) varied from – 0.48 to 0.59, but<br />
no significant values of R (ratio) were<br />
detected (R≥0; p≥0.001) linked to r≥0.4.<br />
Spatial distribution of capture localities is<br />
shown in Figure 1. The related pair (F2-M5)<br />
trap sites are at a distance of about 100 m.<br />
Discussion<br />
The average number of alleles per locus (5.3)<br />
is in the middle part of the range of other<br />
Mustela species, going from the lowest (1.2)<br />
detected in black footed ferret (Mustela<br />
nigripes) (Wisely et al. 2002) to the highest<br />
(11.7) found in stoat (Mustela erminea)<br />
(Fleming et al., 1999). Instead, estimated He<br />
(0.62) is at the highest end of the range, going<br />
from black footed ferret (0.07) (Wisely et al.,<br />
2002) to the stoat (0.83) (Fleming et al. 1999),<br />
and inside the range found in weasel by Pertoldi<br />
et al. 2006 (0.6-0.73).<br />
The analysis of genetic kinship in sampled<br />
population revealed no full siblings, only one<br />
parent-offspring pair and a low degree of<br />
relatedness.<br />
Combining these genetic results with spatial<br />
distribution of traps we generated hypotheses<br />
regarding pattern of dispersal.<br />
The genetic relatedness of the pair F2-M5<br />
represents a relation between sire and female<br />
offspring. The distance between the capture<br />
sites of the two animals (100 m) was inside<br />
the range of the average home range size calculated<br />
for the same population (Magrini et<br />
al. 2009), moreover the absence of siblings<br />
inside the studied population means a spacing<br />
tactic that involves dispersal of the offspring:<br />
these two observations are in agreement with<br />
the hypothesis in which M5 is the father of<br />
F2, but in disagreement with the supposition<br />
in which F2 is the mother of M5 (which<br />
means that M5 didn’t move away from natal<br />
area).<br />
The same absence of siblings between sampled<br />
animals (in particular constituted by<br />
males) means the absence of sex biased dispersal<br />
for female. The other two possibilities<br />
(both sexes dispersal or male dispersal) are in<br />
agreement with the kinship discovered in the<br />
sampled population.<br />
Despite the lack of data about weasels dispersal<br />
in previous studies, our results are yet<br />
in agreement with data on dispersal strategy<br />
of stoats, for which was detected a pattern of<br />
dispersal not sex biased (Erlinge 1977; King<br />
& McMillan 1982; Debrot & Mermod 1983).<br />
For the evaluation of kinship results we were<br />
not able to use data about age class of animals<br />
because of the difficulty in estimating the age<br />
of living weasels: actually the young reach<br />
sexual maturity in only three months<br />
(Sheffield & King, 1994), so from the end of<br />
the breeding season the generations may<br />
appear to overlap, and despite kits, it is impossible<br />
to determine an age class with any confidence<br />
(King 2007). Another problem is the<br />
lack of data about females (only three were<br />
captured during the study), that didn’t permit<br />
to clarify prospective sex biased dispersal.<br />
Weasels were described as an r-selected<br />
species (Sandell 1984; Stenseth 1985) with<br />
short life span, high natural mortality in the<br />
first year (75%-90%) (King 1980, 2007;<br />
Sheffield & King 1994; McDonald & Harris<br />
1998) but also rapid production of young and<br />
high population turn-over: so natural populations<br />
suffer great numerical fluctuations that<br />
involve local extinctions and recolonizations<br />
in which a different set of resident animals is<br />
observed every year (King 1983, 1989, 2007).<br />
Even if these ecological and biological traits<br />
seem to converge in an opportunistic philopatry<br />
strategy (Waser & Jones 1983), data from<br />
this study disprove this hypothesis: the lack<br />
of sibling kinship in the sampled population<br />
can suggest the presence of dispersal strategy,<br />
probably promoted by survival of resident<br />
animals in the second life year.<br />
Also Pertoldi et al. (2006) found a high<br />
genetic variance in wild weasel population,<br />
that does not agree with an high population<br />
turnover and density fluctuations (Caballero<br />
1994).<br />
Genetic structure is strongly influenced by<br />
patterns of individual movement and reproduction<br />
as stressed by Cutrera et al. (2005):<br />
molecular studies seem the most useful way<br />
to investigate these patterns in very elusive<br />
small carnivore species.<br />
ecologia mediterranea – Vol. 38 (2) – 2012