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all geography including DSDP/ODP Sites and Legs
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sedimentary structures
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Puma concolor
Evidence of Puma concolor and Dasypus novemcinctus interactions. A ) C...
ARMADILLO OSTEODERMS ALTERED BY DIGESTION AND HOW TAPHONOMY CAN HELP TAXONOMY
Pleistocene mammals from Extinction Cave, Belize
(A) Panthera atrox . 77570. Left radius, midshaft portion, ends rounded by...
Relative abundances of anatomical elements recovered from the sediment (TOT...
Map showing the geographic distribution of Dasypus novemcinctus and Puma...
Figure 7. Body size (log 10 ) distribution of hypercarnivorous species in...
A POSSIBLE SMILODON (MAMMALIA, FELIDAE) COPROLITE FROM THE PLEISTOCENE OF ARGENTINA
Hyena as a predator of small mammals? Taphonomic analysis from the site of Bois Roche, France
Long in the tooth: evolution of sabertooth cat cranial shape
Late Pleistocene records of felids from Medicine Hat, Alberta, including the first Canadian record of the sabre-toothed cat Smilodon fatalis
Revisiting Russell’s troodontid: autecology, physiology, and speculative tool use 1
Dinosaurian and mammalian predators compared
Ecomorphological determinations in the absence of living analogues: the predatory behavior of the marsupial lion ( Thylacoleo carnifex ) as revealed by elbow joint morphology
Early Eocene Leptictida, Pantolesta, Creodonta, Carnivora, and Mesonychidae (Mammalia) from the Eureka Sound Group, Ellesmere Island, Nunavut
THE PSILONICHNUS ICHNOCOENOSE, AND ITS RELATIONSHIP TO ADJACENT MARINE AND NONMARINE ICHNOCOENOSES ALONG THE GEORGIA COAST
U.S. military installations as bioreserves: A case study from Fort Hood, Texas
Abstract U.S. military installations increasingly have become de facto bioreserves as the result of legacy and current land uses, urbanization, and historical siting of installations. The relative value of military lands as bioreserves compared to land holdings of other federal agencies is not proportional to total land area. Ironically, a significant reason that U.S. military installations have become important bioreserves is that they were not established with the purpose of conserving or extracting natural resources. This historical factor has resulted in a broad representation of U.S. ecoregions on military lands and largely has shielded those lands from the habitat loss and degradation that has occurred in surrounding regions due to urbanization, agricultural development, and other non-military land uses. Fort Hood, Texas, is used as a case study to illustrate the characteristics of military installations that fit the model for bioreserves as areas for conservation of biological resources and processes in the context of human use of the environment. A major current challenge for management of natural resources on military lands is that the value of U.S. military lands as bioreserves is increasing as surrounding habitats and natural communities continue to be degraded.