In the Neotropics, dry forests are regarded as ecosystems with high priority for conservation1. Some species inhabit exclusively this ecosystem, resisting high temperatures and marked water restrictions during great part of the year 1,2. Yet the areas that contain dry forests have also supported large human settlements, creating a long history of transformation and loss of biodiversity1,3.
Alarmed by the threats that affect dry forests in Colombia4 and the lack of knowledge about their dynamics and functioning5,6, regional investigators started a national strategy for monitoring the vegetation of dry forests (BSTCol) in 2013. The goal of this initiative is to generate scientific data that may be useful for the integrated management of the ecosystem, especially in the current situation of change and complex socioecological scenarios it faces7.
These monitoring efforts contribute with high quality information that must be the base for decision making in terms od dry forest conservation. Consequently, it is considered that permanent monitoring of vegetation will account for a systematic process of obtaining and analyzing data that will not only explore trends in changes of attributes proper to the species and plant communities in time, but also allow for evaluating the effects different conservation strategies in Colombia have on the integrated management of its biodiversity.
Up to now, based on the analysis of recorded information for the first group of data obtained, 623 species of plants (33,559 individuals), including trees, bushes, palms, lianas, and cacti, have been monitored in all plots (62±29 species/ha). When overlapping the plots with the Sistema Nacional de Áreas Protegidas (National System of Protected Areas, Sinap for its initials in Spanish), it was found that both the areas with strict protection and private conservation initiatives shelter a greater number of species than the forests without management efforts. In Natural National Parks and Regional Parks there are approximately 72 species/ha, in Private Reserves of the Civil Society around 74 species/ha, and in private buildings 51 species/ha.
Nevertheless, there is a high floral exclusiveness and unity in each monitored site and most regions contain endemic species. These facts highlight the importance of Sinap in the integrated management of biodiversity in dry forests and the need of proposing alternative conservation plans for plants in those private areas that currently lack a management strategy based on the integration to productive landscapes in each site.
Even though this initiative is still in its preliminary phase, in the future conservation needs derived from the analysis of plant dynamics, functioning, and response capacities in the face of transformation may be determined thanks to permanent monitoring.