All sites chosen had vegetation coverage adequate to localize BN plants of all sizes, including seedlings. We avoided recently abandoned crops because of their excessively dense and entangled vegetation.

However, we sampled fallows older than ten years because they already show some stratification and, like the active crops, make the census easier to conduct. We also included some sites currently used as pastures. Pastures, an integral part of the local landscape, often succeed crops. The pastures are planted not only for cattle, but also as a grazing area for horses, donkeys, and mules, animals that represent a useful work force during the BN harvest and other daily activities. The information obtained from the interviews about the number of cultivation cycles was later confirmed using a temporal sequence of Landst5 satellite images that were available this website with minimum cloud coverage above the studied sites. We used the multi-spectral TM sensor, comprising bands 5R4G3B

of the 226/060 scene from 1985, 1991, 1996, 1997, 1998, 1999/2000, 2003, 2004, 2007 and 2008 images. The 2008 image was georeferenced with ground truth points collected during fieldwork (GPS Garmin 60 CS×), and the previous images were georeferenced based on the current one and adjusted using natural and man-made landscape features until a root-mean-square error lower than one pixel size was attained. Our informers reported accurately about the last, penultimate and ante-penultimate agricultural use cycles on their fields. However, information prior to the ante-penultimate cycle occasionally sounded vague or divergent. At the same time, the limited www.selleckchem.com/products/pci-32765.html temporal sequence of available images could not confirm cultivation patterns with certainty beyond the ante-penultimate cultivation cycle. For that reason, we restricted the number of cultivation cycles to those events of one, two and three or more cultivation cycles we were able to distinguish. Fallow sites were also classified according to the number of previous slash-and-burn RAS p21 protein activator 1 cycles. We added one more cycle to the total for the site in cases of fallows having signs of prior disturbance

verified in the oldest available image (light-green pixel sensor response in the 1985 scene). We used a different counting method for pasture cycles. Because active pastures are burned repeatedly every two or three years, they never develop the vegetation coverage needed to support the natural disperser activity (Silvius and Fragoso, 2003). As chronically disturbed sites (Uhl et al., 1988), pastures were counted as a single continuous cycle from their establishment in the forest or as a second or third cycle if located in sites previously used for SC. In view of that adjustment, we sampled nine sites in a first-use cycle (established directly after clearance of mature forest), nine sites in a second-use cycle (one previous fallow), and 22 sites after three or more cultivation cycles (two or more previous fallows).