Comparing species checklists across countries can be important for determining the relative uniqueness of each country, which can be conveniently defined on the basis of the number of species occurring only in that country or, at most, in one of its neighboring countries. Production of accurate country checklists is complicated by the fact that, especially in scientifically neglected regions, the knowledge of the distribution of many species is unsatisfying. When distribution of a given species is insufficiently known, typically there may be apparent gaps in its distribution range. These species are defined here as 'gap species'. In this paper, we analyze the country checklists for rodents and insectivores of the African continent with the aims of (i) identifying the countries having a higher taxonomic uniqueness; (ii) highlighting countries where more research is needed; (iii) producing a list of gap species; and (iv) determining the ecological correlates of being a gap species. For both mammal groups, the important countries because of their low numbers of shared species were D.R. Congo, Cameroon, Sudan, Kenya, Tanzania, and South Africa. The countries with highest percentages of endemic taxa were Kenya, South Africa, Somalia and Tanzania for insectivores, and Ethiopia and South Africa for rodents. The number of gap species per country was 0-5 for both insectivores and rodents, with the only exceptions of Togo (12) and Benin (15). Apart from Togo and Benin, the main gap countries for rodents were Nigeria, Chad, Gabon, Burundi, and Rwanda, and for insectivores were Niger and Chad. In both groups, the number of gap species per country was independent on the country area, and both range and body sizes did not influence the probability for a species to have distribution gaps. However, most gap species were tropical forest inhabitants. The biogeographic and conservation implications of these data are discussed

3Comparative aspects of the demography were investigated in three distinct populations of the ecologically 4 poorly studied rodent Eliomys quercinus, in Spain and Italy. Maximum longevity was observed in a Spanish 5 female (at least 2 years and 4 months survival). For all the populations under study, various closed 6 populations models and the Robust design model gave similarly reliable estimates for population size, with 7Jolly-Seber estimates being considerably less reliable. The same result also emerged for survival and 8 capture probabilities estimates, but with less profound differences between Jolly-Seber and the closed 9 models with Robust design. Average density showed considerable oscillations over the years and across 10

The causes of spatial distribution gaps for a given species may be either both natural (habitat discontinuities) or non-natural (local extinctions, inaccurate knowledge). These species are defined as 'gap species'. We analyzed the country checklists for African chelonians in order to identify both gap species and gap countries. We also compared patterns observed in chelonians with those observed in African small mammals. Species richness was highest in South Africa, Congo, Nigeria, Tanzania, Angola and Ghana, and the countries exchanging the smallest number of species with neighboring countries were South Africa and Congo. The main gap countries were Togo, Benin, and Congo. Moist savannahs, tropical forests, and swamp areas were inhabited by significantly higher numbers of gap species. Body size of gap species was significantly larger than that of non-gap species, possibly due to bush-meat consumption. Increases in the number of gap species per country were significantly correlated between chelonians and small mammals. There was a significantly positive relationship of turnover rates by paired countries between chelonians and rodents as well as between chelonians and insectivores, and the mean turnover rates by country were highest in Sudan and Chad, whereas the whole southern portion of Africa and part of West Africa had low mean turnover rates. The high number of gap species in Congo, Central African Republic (C.A.R.), and Cameroon may be due to suboptimal research, and in Togo and Benin may depend on the Dahomey Gap. The tropical forests and the moist savannahs are the most important habitats for both groups.