Agriculture, Ecosystems and Environment 139 (2010) 174–180
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Agriculture, Ecosystems and Environment
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Land-use/cover dynamics in Northern Afar rangelands, Ethiopia
Diress Tsegaye
a,b,∗
, Stein R. Moe
a
, Paul Vedeld
c
, Ermias Aynekulu
d
a
Department of Ecology and Natural Resource Management, Norwegian University of Life Sciences, P.O. Box 5003, 1432 ÅS, Norway
b
Department of Animal, Rangeland and Wildlife Sciences, Mekelle University, P.O. Box 231, Mekelle, Ethiopia
c
Department of International Environment and Development Studies, Noragric, Norwegian University of Life Sciences, P.O. Box 5003, 1432 ÅS, Norway
d
Center for Development Research (ZEF c), University of Bonn, Walter-Flex-Str. 3 53113 Bonn, Germany
article info
Article history:
Received 13 January 2010
Received in revised form 26 July 2010
Accepted 27 July 2010
Available online 19 August 2010
Keywords:
Afar pastoralists
Agriculture
Drought
Dry-season grazing
Livelihoods
Vegetation cover
abstract
This study uses a combination of remote sensing data, field observations and information from local
people to analyze the patterns and dynamics of land-use/cover changes for 35 years from 1972 to 2007 in
the arid and semi-arid Northern Afar rangelands, Ethiopia. A pixel-based supervised image classification
was used to map land-use/cover classes. People’s perceptions and ecological time-lines were used to
explain the driving forces linked to the changes. A rapid reduction in woodland cover (97%) and grassland
cover (88%) took place between 1972 and 2007. Bushland cover increased more than threefold, while the
size of cultivated land increased more than eightfold. Bare land increased moderately, whereas bushy
grassland and scrubland remained stable. According to accounts from local people, major events that
largely explain the changes include: (1) severe droughts in 1973/74 and 1984/85; (2) increase in dry
years during the last decade; and (3) immigration and increased sedentarization of pastoralists. If the
present land-use/cover change were to continue, coupled with a drier climate, people’s livelihoods will
be highly affected and the pastoral production system will be under increasing threat.
© 2010 Elsevier B.V. All rights reserved.
1. Introduction
An estimated 4.7 million km
2
grassland areas and 6 million km
2
of forests/woodland, have been converted to croplands worldwide
since 1850 (Lambin et al., 2001, 2003). In recent years, African
grassland, woodland, and other vegetated areas have increasingly
been converted into cropland (Millennium Ecosystem Assessment,
2005). For instance, an estimated 3.4 million km
2
of woody vege-
tation in dryland zones of Africa have become degraded through
human activities such as agricultural expansion and deforestation
(Kigomo, 2003).
Land-use shifts caused by external and internal drivers have
influenced many traditional resource management regimes in arid
and semi-arid areas where often a pastoral way of life has been the
tradition (Campbell et al., 2005; Reid et al., 2004). The equilibrium
paradigm, which states that ecosystem regulation is maintained
in a stable way through negative feedback mechanisms, guided
most rangeland management policy until the 1970s (Briske et al.,
2003). Based on the concept of ‘tragedy of the commons’ (Hardin,
1968), pastoralism was considered as an environmentally destruc-
tive resource exploitation strategy that resulted in overstocking
∗
Corresponding author at: Department of Ecology and Natural Resource Man-
agement, Norwegian University of Life Sciences, P.O. Box 5003, 1432 ÅS, Norway.
Tel.: +47 64965793; fax: +47 64965801.
E-mail addresses: diress.alemu@umb.no, diress62@yahoo.com (D. Tsegaye).
and the disruption of a perceived ecological equilibrium. This dom-
inant paradigm was increasingly criticized in the 1980s partly
due to a growing concern that interventions based on equilib-
rium assumptions were inappropriate for some pastoral systems
(Behnke and Scoones, 1993; Ellis and Swift, 1988; Sandford, 1983).
Current theoretical evidence indicates that both equilibrium
and non-equilibrium dynamics occur in ecosystems across both
spatial and temporal dimensions (Briske et al., 2005; Oba et al.,
2000; Wessels et al., 2007). Although conclusive empirical evidence
does not exist to terminate the debate, rangeland degradation is
still a widely occurring phenomenon in many African rangelands,
threatening national economic values and also the lifestyles of pas-
toralists. Despite all the rhetoric and the policy discussions, the
current pace of degradation is unprecedented both in arid and
semi-arid areas (Millennium Ecosystem Assessment, 2005).
There have been some studies of land-use/cover changes at
regional or local levels, but they often deal exclusively with quan-
tifying land-use/cover changes using remote sensing tools or they
focus on causes of land-use/cover changes through socio-economic
surveys. Mapping spatial changes using remote sensing tools gives
quantitative descriptions but does not explain or provide under-
standing of the relationship between the patterns of change and
their driving forces (Olson et al., 2004). Some recent advances in
remote sensing play a major role in linking social models with
the spatial dynamics of land-use changes (e.g., Mottet et al., 2006;
Serneels and Lambin, 2001; Serra et al., 2008). However, studies
such as these linking land cover changes with drivers are rare
0167-8809/$ – see front matter © 2010 Elsevier B.V. All rights reserved.
doi:10.1016/j.agee.2010.07.017