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Figure 12 in Type Specimens of Non-fossil Mammals in the Australian Museum, Sydney

Figure 12. Skull of AM B.9579, holotype of Sminthopsis monticola Troughton, 1965a. (Photography by Sally Cowan).

Figure 6 in Type Specimens of Non-fossil Mammals in the Australian Museum, Sydney

Figure 6. Skull of AM PA.658, syntype of Antechinus allanii Krefft, 1872b. (Photography by Stuart Humphreys).

Figure 17 in Type Specimens of Non-fossil Mammals in the Australian Museum, Sydney

Figure 17. AM M.2554, syntype skull of Perameles moresbyensis Ramsay, 1877a. (Photography by Stuart Humphreys).

Figure 24 in Type Specimens of Non-fossil Mammals in the Australian Museum, Sydney

Figure 24. AM M.2301, holotype skull of Trichosurus caninus nigrans Le Souef, 1916. (Photography by Sally Cowan).

Figure 11 in Type Specimens of Non-fossil Mammals in the Australian Museum, Sydney

Figure 11. Alcoholic body of AM B.9579, holotype of Sminthopsis monticola Troughton, 1965a. (Photography by Sally Cowan).

Figure 20 in Type Specimens of Non-fossil Mammals in the Australian Museum, Sydney

Figure 20. AM M.5732, holotype skin of Phascolarctos cinereus victor Troughton, 1935a. (Photography by Sally Cowan).

Figure 15 in Type Specimens of Non-fossil Mammals in the Australian Museum, Sydney

Figure 15. AM M.6609, holotype skin of Isoodon arnhemensis Lyne & Mort, 1981. (Photography by Sally Cowan).

Figure 5 in Type Specimens of Non-fossil Mammals in the Australian Museum, Sydney

Figure 5. Skin mount of AM PA.658, syntype of Antechinus allanii Krefft, 1872b. (Photography by Sally Cowan).

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Fig. 1 in Population Dynamics Of Arboreal And Terrestrial Small Mammals In A Tropical Rainforest, Sarawak, Malaysia

Fig. 1. Temporal patterns at Lambir Hills National Park, Sarawak, Malaysia, from August 1997 to December 2005. (a) percentage of fruiting trees obtained by phenology observation (%; black circle), together with weight of dried fruits obtained by seed traps from November 2000 to December 2005 (g/m2; white circle); (b) population dynamics per 100 trapnights of arboreal and terrestrial small mammals; (c) percentage of the two age classes (immature and adult) of Maxomys rajah. Total numbers of captured M. rajah at each census were shown.

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Fig. 2 in A Camera Trapping Inventory For Mammals In A Mixed Use Planted Forest In Sarawak

Fig. 2. Some of the photographs taken by camera during the study period showing how animals respond to a lure. A, Helarctos malayanus, Malayan Sun Bear; B, Sus barbatus, Bearded Pig; C, Viverra tangalunga, Malay Civet / Tangalung.

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Fig. 1 in A Camera Trapping Inventory For Mammals In A Mixed Use Planted Forest In Sarawak

Fig. 1. Location of Planted Forest Zone within Bintulu Division in Sarawak, Malaysia. Planted Forest Zone is indicated in dark striped areas in center of map.

Fig. 4 in Mammal Diversity And Conservation In A Small Isolated Forest Of Southern Thailand

Fig. 4. Activity periods of photo-captured animals (N>10) in the Hala-Bala Wildlife Sanctuary, Thailand, from Nov.2004 to Oct.2007. Species are listed in order of decreasing frequency of diurnal activity. Numbers in parentheses indicate sample size.

Fig. 3 in Mammal Diversity And Conservation In A Small Isolated Forest Of Southern Thailand

Fig. 3. Rarefaction curves for photo-captured animal assemblages in primary and logged forests over 3 years (thick line: first year; open circles: second year; solid circles: third year) in the Hala-Bala Wildlife Sanctuary, Thailand. The dotted line represents the 95% CI for the first year. For clarity, the 95% CI for the second and third years are not presented.

Fig. 1 in Mammal Diversity And Conservation In A Small Isolated Forest Of Southern Thailand

Fig. 1. Hala-Bala Wildlife Sanctuary (Bala forest) in southern Thailand, and the road cutting through the forest and associated trails on either side, as used by Gale and Thong-Aree (2006).

Fig. 2 in Mammal Diversity And Conservation In A Small Isolated Forest Of Southern Thailand

Fig. 2. Rarefaction curves for photo-captured animal assemblages in three forest types (thick line: primary forest; open circles: logged forest; solid circles: hill forest) in the Hala-Bala Wildlife Sanctuary, Thailand, from Nov.2004 to Oct.2007. The dotted line represents the 95% CI for the primary forest. For clarity, the 95% CI for the logged and hill forests are not presented.

Fig. 169 in Mammals Of The Rio Juruá And The Evolutionary And Ecological Diversification Of Amazonia

Fig. 169. Geological crosssection through the central portion of the Rio Juruá illustrating the position of the underlying structural Iquitos Arch relative to Upper Central and Lower Central sample sites, the positional shift of major soils from the downriver Alter do Chãu to upriver Solimes formations and position and depths of the upper Acre Subbasin and lower Central Amazon Subbasin. The geographic position of drill core sites from the Brazilian oil consortium, Petrabras, are indicated. Redrawn from Fig. 10 in volume 15 of the Projeto RadamBrasil (1977).

Fig. 170 in Mammals Of The Rio Juruá And The Evolutionary And Ecological Diversification Of Amazonia

Fig. 170. Hypothesis of area relationships for lowland tropical forests of South America based on analyses of avian phyletic and distributional data (from Cracraft and Prum, 1988).

Fig. 166 in Mammals Of The Rio Juruá And The Evolutionary And Ecological Diversification Of Amazonia

Fig. 166. Sample localities and distribution of haplotypes of the cytochromeb gene for the spiny tree rat Mesomys hispidus (above) and two species of terrestrial spiny rats Proechimys simonsi (middle) and P. steerei (below) along the Rio Jurua´. Single haplotypes shared among localities are indicated by ellipses connecting them. The number of haplotypes unique to each locality is also indicated.

Fig. 161 in Mammals Of The Rio Juruá And The Evolutionary And Ecological Diversification Of Amazonia

Fig. 161. Phenogram of Jaccard's similarity coefficients in comparisons of species composition between all documented species of marsupials, murid rodents, and echimyid rodents from each of 21 lowland Neotropical forest sample sites (see text). Terminal branches are identified by locality, as in the map (fig. 162). Mantel's matrix correlation coefficient for the association between the similarity matrix and the cophenetic correlation matrix is 0.946, p <0.001.

Fig. 162 in Mammals Of The Rio Juruá And The Evolutionary And Ecological Diversification Of Amazonia

Fig. 162. Sample sites in lowland neotropical forests for which reasonably complete species inventories are available for marsupials, murid rodents, and echimyid rodents (data largely from Voss and Emmons, 1996; see text). Regional groupings of localities, based on the phenogram of Jaccard's similarity coefficients in fig. 161, are drawn to indicate geographic relationships in community composition Localities outside of the Rio Juruá are identified by letters corresponding to the names given in the phenogram, fig. 161.