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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

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