Fernando Pulido

Dr. Fernando Pulido

Institute for Silvopastoral Research (INDEHESA), Universidad de Extremadura, 06006 Badajoz, Spain

Research Focus & Metrics

Academic Career Length

30Years (1997-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

View All Publications
1 January 2005 in Écoscience
Verified
Journal Article
Closed access
Fernando PulidoFernando Pulido
Fernando Pulido
MDMario Díaz
Mario Díaz

1 June 2001 in Forest Ecology and Management
Verified
Journal Article
Closed access
Fernando PulidoFernando Pulido
Fernando Pulido
MDMario Dı́aZ
Mario Dı́aZ
STSebastián J Hidalgo de Trucios
Sebastián J Hidalgo de Trucios

1 March 2003 in Environmental Conservation
Verified
Journal Article
Closed access
PDF file
Tobias PlieningerTobias Plieninger
Tobias Plieninger
Fernando PulidoFernando Pulido
Fernando Pulido
WKWerner Konold
Werner Konold
Dehesas, rangelands occupied by scattered oak trees and characterized by silvopastoral uses, cover about 3.1 million ha in south-western Spain. There is considerable debate about the long-term persistence of holm oak (Quercus ilex) populations in dehesas, since most stands are overaged and seedlings and saplings are sparse. The forest cycle has been disrupted in most dehesas. Regeneration has been inhibited since stands were opened for agriculture and grazing. Oak diameters from three land-use groups (young dehesa [YD], middle-aged dehesa [MD], and old dehesa [OD]) in Cáceres Province, Spain, were compared. These groups differed in the age of the land-use system, i.e. time since the original Mediterranean forest was cleared. The dehesa systems were established about 80 (YD), 150 (MD) and 500 (OD) years ago. An analysis of 66 holm oak cross sections revealed a close correlation (r2 = 91.2%) between tree rings and diameters, so that diameter seems to be a reliable indicator of tree age. Nested analysis of variance showed significant variation in diameters between the land-use groups. There is generally a positive relationship between tree age and the age of agrosilvopastoral use of the dehesas. Sparse holm oaks in the dehesas are primarily remnants from the first forest cycle. Local differences in growth conditions (for example soil quality and tree density) contribute further significant diameter variation on a between-plot level. Diameter structure of abandoned dehesas showed two peaks and a high proportion of trees in the smallest size class. This indicates that the forest degradation process is reversible. An effective regeneration policy should promote a rotating 20- to 30-year set-aside of dehesa parcels.

24 June 2014 in Nature Communications
Verified
Journal Article
Open access
PDF file
MSManuel K. Schneider
Manuel K. Schneider
GLGisela Lüscher
Gisela Lüscher
Philippe JeanneretPhilippe Jeanneret
Philippe Jeanneret
MAMichaela Arndorfer
Michaela Arndorfer
YAYoussef Ammari
Youssef Ammari
FHFelix Herzog
Felix Herzog
Organic farming is promoted to reduce environmental impacts of agriculture, but surprisingly little is known about its effects at the farm level, the primary unit of decision making. Here we report the effects of organic farming on species diversity at the field, farm and regional levels by sampling plants, earthworms, spiders and bees in 1470 fields of 205 randomly selected organic and nonorganic farms in twelve European and African regions. Species richness is, on average, 10.5% higher in organic than nonorganic production fields, with highest gains in intensive arable fields (around +45%). Gains to species richness are partly caused by higher organism abundance and are common in plants and bees but intermittent in earthworms and spiders. Average gains are marginal +4.6% at the farm and +3.1% at the regional level, even in intensive arable regions. Additional, targeted measures are therefore needed to fulfil the commitment of organic farming to benefit farmland biodiversity.


8 February 2007 in Agroforestry Systems
Verified
Journal Article
Closed access
PDF file
GMGerardo Moreno
Gerardo Moreno
JOJ. J. Obrador
J. J. Obrador
EGE. García
E. García
ECE. Cubera
E. Cubera
María Jesús Montero-ParejoMaría Jesús Montero-Parejo
María Jesús Montero-Parejo
CDC. Dupraz
C. Dupraz