We reviewed the scientific literature published from 1940 to 2002 on Latin American (Mexican and Central and South American) deer (Mammalia: Cervidae), focusing on conservation status and prediction of geographic distributions. The extant Latin American deer are the most diverse deer assemblage in the world (Cervinae: one genus, one species: Elk [Cervus elaphus]; Odocoilineae: six genera, 18 species: White-tailed deer [Odocoileus virginianus], mule deer [O. hemionus], marsh deer [Blastocerus dochotomus], pampas deer [Ozotoceros bezoarticus], huemul [Hippocamelus bisulcus], taruca [Hippocamelus antisensis], greater pudu [Pudu mephistophiles], lesser pudu [Pudu pudu], and six recognized species of brocket deer [Mazama americana, M. gouazoubira, M. nana, M. bricenni, M. chunyi, and M. rufina] as well as three recently proposed species [M. pandora, M. rondoni, and M. bororo]). Within this group, three genera (Odocoileus, Hippocamelus, and Blastocerus) have been well studied, whereas the genus Mazama, P. puda, P. mephistophiles, and H. antisensis have received little attention. The marsh deer, pampas deer, taruca, huemul, lesser pudu, and two Mazama species (Mazama nana and M. bororo) are the most endangered species. They are each listed as Convention International for the Trade of Endangered Species Appendix I and are considered by the International Union for Nature Conservation to be near threatened or endangered. We updated or created distribution maps for these species. Current research predominantly centres on easily available species (e.g., white-tailed deer in Mexico) or endangered species (e.g., marsh deer in Brazil). In contrast, the ecology and conservation status of the pudu, taruca, and Mazama sp. remain largely unknown.

Secondary forests are extensive in the tropics. Currently, these plant communities are the available habitats for wildlife and in the future they will possibly be some of the most wide-spread ecosystems world-wide. To understand the potential role of secondary forests for wildlife conservation, three ungulate species were studied: Mazama temama, Odocoileus virginianus and Pecari tajacu. We analyzed their relative abundance and habitat use at two spatial scales: (1) Local, where three different successional stages of tropical deciduous forest were compared, and (2) Landscape, where available habitats were compared in terms of landscape composition (proportion of forests, pastures and croplands within 113 ha). To determine the most important habitat-related environmental factors influencing the Sign Encounter Rate (SER) of the three ungulate species, 11 physical, anthropogenic and vegetation variables were simultaneously analyzed through model selection using Akaike’s Information Criterion. We found, that P. tajacu and O. virginianus mainly used early successional stages, while M. temama used all successional stages in similar proportions. The latter species, however, used early vegetation stages only when they were located in landscapes mainly covered by forest (97%). P. tajacu and O. virginianus also selected landscapes covered essentially by forests, although they required smaller percentages of forest (86%). All ungulate species avoided landscape fragments covered by pastures. For all three species, landscape composition and human activities were the variables that best explained SER. We concluded that landscape is the fundamental scale for ungulate management, and that secondary forests are potentially important landscape elements for ungulate conservation

Surveillance for evidence of West Nile virus (WNV) infection in Morelet’s crocodiles (Crocodylus moreletii) was conducted in Campeche State, Mexico, in 2007. Sera from 62 crocodiles (32 free-ranging and 30 captive) were assayed for antibodies to WNV by epitope-blocking enzyme-linked immunosorbent assay. Antibodies to WNV were detected in 13 (41%) wild and nine (30%) captive crocodiles, and the overall antibody prevalence was 35%. Although evidence of WNV infection in captive crocodiles has been reported in Mexico, we provide the first evidence of WNV exposure in wild crocodiles in Mexico.

Oogenic development and gonotrophic cycle of Aedes aegypti and Aedes albopictus in laboratory