- Open Access
Land use/cover dynamics and its drivers in Gelda catchment, Lake Tana watershed, Ethiopia
Environmental Systems Research volume 6, Article number: 4 (2018)
The demand for meeting local food production has caused farmlands to expand at the cost of natural forests and grasslands in the Ethiopian highlands. However, empirical evidences on rate and patterns of LULC dynamics, and major driving forces in highlands of Ethiopia at catchment level were rare to contribute to design effective land management options. This study was to analyze the rate and patterns of LULC dynamics, and identify major driving forces in the Gelda catchment.
Six different LULC maps derived from aerial photographs and Landsat images were produced, and comparisons were made. The results indicated that the study catchment has undergone significant LULC alterations and transformations since late 1950s. Farmlands and settlement were expanded by 57.7% while shrubs, forests and grasslands were declined by 18.6, 83.8 and 53.5% over the entire study period, respectively. The magnitude of initial grasslands and farmlands converted into degraded land seems small; however these can significantly cause an irreversible damage to the soil resources. The combinations of land reform of 1975, forest development and villagization program 1980s, civil war, frequent changes in political structure, and population pressure were the major driving forces of LULC change.
Therefore, the GIS and remote sensing based change detection matrix analysis technique could provide useful baseline information to understand the spatiotemporal patterns of land use transitions caused by the major driving forces thereby sustainable land management planning is possible.
Local changes in land use and land cover (LULC) affect life support functions and human livelihoods (Lambin et al. 2001; Lambin and Geist 2006). It has diverse environmental impacts by negatively affecting water supply, reservoir storage capacity, agricultural productivity and ecology of a region (Sharma et al. 2011). In most developing countries, the demands for meeting local food production caused agricultural lands expansion at the expense of natural forests and grasslands (Lambin et al. 2003). Local level studies undertaken in highlands of Ethiopia suggest that a presence of significant LULC changes were caused by a combination of varying factors depending on each locality condition (Hassen et al. 2015; Eyayu et al. 2009; Woldeamlak and Sterk 2005; Eleni et al. 2013; Mohammed 2011; Woldeamlak 2002).
Increased deforestation and poor farm management practices has led to accelerated soil erosion and land degradation in the Ethiopian highlands (Mohammed et al., 2005; Hurni et al. 2005; Hassen et al. 2015). These are, particularly, common in areas where high population pressure exists whose livelihoods directly depend on the exploitation of natural resources in rural areas (Woldeamlak and Sterk 2005). Farmland/settlements and bushlands/degraded lands were expanding appreciably, while grasslands and forest areas have been diminished largely driven by population pressures, economic factors and policy issues (Woldeamlak 2002; Getachew et al. 2011; Tsehaye and Mohammed 2013; Eleni et al. 2013; Hassen et al. 2015; Alemu et al. 2015). Similarly, significant expansions of urban built-up were accompanied by substantial decline in forest, grass and shrub lands (Mohammed 2011). These studies supported that LULC changes have implications for environmental degradation such as soil erosion, soil quality deterioration, decreasing available water and the subsequent drying-out of water reservoirs.
Increasing rates of forest conversion, unsustainable agricultural land use and severe soil erosion are the major factors characterizing land degradation in the highlands of Ethiopia (Mekuria 2005). Despite efforts made to overcome deforestation and the resulting land degradation in Ethiopia, as EFAP 1993, the extent of forests was much higher from 40% at the beginning of the twentieth century, 16% in the 1950s, 3.1% by 1982, only 2–3% in 1990s, and 3.56% in 2004 (Badege 2001; Wubalem 2012). That means, although the attempts to rehabilitate areas under intense deforestation and degraded as part of national campaign to conserve soil and water in different parts of Ethiopia have been done; success has been limited to date. Accordingly, some remnant stands of natural forests are mainly confined to religious sites, along rivers and streams, and on peaks of hills where crop cultivation is difficult in the highlands of Ethiopia (Warra et al. 2013). This is due to the fact that agriculture and rural settlement has remained the predominant and ever expanding LULC classes between 1965 and 2007 caused by a variety of natural and man-made drivers of change.
The major driving forces of human-induced change in LULC form a complex system of dependencies, interactions and feedback loops at different spatiotemporal scales (Agarwal et al. 2002; Verheye 2007). These complexity calls for multidisciplinary analyses, primarily focused on biophysical attributes (e.g. topographic or soil type), and wide range of socio-economic drivers of change (Veldkamp and Lambin 2001). Driving force of landscape change is determined by the spatiotemporal and institutional scale of the system under study (Bürgi et al. 2004). These driving forces of landscape change involve land cover (climate, topography and soil characteristics) and land use (human induced) processes, such as natural (biophysical) and man-made driving forces, i.e., socioeconomic, political, technological, and cultural (Bürgi et al. 2004; Sherbinin 2002; Lambin et al. 2001). Cultural or man-made drivers may also trigger events as important as biophysical drivers (Lambin et al. 2003).
The mounting pressures on the natural forest, shrubs and grasslands by unsustainable land uses, in the study area, have witnessed spatiotemporal changes in LULC patterns. However, studies of LULC dynamics using change detection analysis to explain the land use transition, i.e., net loss and/or gain of each LULC classes over space and time at this level are rare in the northwestern highlands of Ethiopia. This study is, therefore, crucial for researchers to contribute on the limited literature on the subject by providing empirical evidences on rate and patterns, and major driving forces of LULC dynamics in highlands of Ethiopia at catchment level; which can contribute to design effective land management options. It can also provide insights into the major contributors of land use transitions and a baseline study for examining their implications on soil erosion potential, soil characteristics and suitability status of the land for sustainable rainfed agriculture in the highlands of Ethiopia. Therefore, the main purpose of this analysis is to provide empirical evidences on rate and patterns, and identify major driving forces of LULC dynamics at watershed level; and thereby designing a more effective land management options will be possible.
Materials and methods
Study area description
The Gelda catchment is located between 11°38′14″ and 11°46′15″N latitude, and 37°25′54″ and 37°41′29″E longitude. It has an area of 26,264 hectares, covering about 2.2% of the Lake Tana watershed. It is drained by a stream named as Gelda (from where the name of watershed is given) flowing into Lake Tana from west direction (Fig. 1). The landform of the catchment reflects its geological history where uplifting force created an initial elevated landmass and the subsequent outpouring of basaltic lava provided a thick protective cap and added on to the elevation (Eleni et al. 2013). According to the report of Geological Survey of Ethiopia (GSE 1996), the catchment generally comprises materials ranges from alkaline to transitional basalts that often forming shield volcanoes, with minor trachyte and phenolite flows called “Tarmaber Gussa Formation” in southeast and eastern parts of the catchment formed during the Oligocene to Miocene epochs of the Tertiary period. The western and northwestern parts of the catchment consist of alluvial and lacustrine deposits of the Quaternary period.
The altitude ranges from 1780 to 2481 meters above sea level. The slope gradient is dominated by gentle slope (0–7.6%) covering about 48.5% (12,682 ha) and moderately steep (7.7–16%) with 37.13% (9714 ha) of the catchment. The steep (16.2–30.2%) and very steep (>30.3%) slope gradients cover about 11.22% (2936 ha) and 3% (787 ha) respectively, commonly found in the southeastern and southern corners of the catchment. Gleysols (54.9%) and Nitisols (30.5%) form the major soil types of the catchment (FAO 1997). Gleyosols are poorly drained with seasonal water accumulation (Driessen and Deckers 2001). The other soils are commonly found on the sloping lands.
The type of climate is generally sub-tropical with average total annual rainfall amount of 1453 mm showing a high inter-annual variability (Hurni 1998). The available rainfall records for the period between 1961 and 2014 records showed that the pattern is predominantly uni-modal. The main rainy season category, June to October, accounts for about 90% of the total annual rainfall (Fig. 2). The highest mean monthly temperature (30 °C) is recorded in April whereas the minimum (8 °C) in December with mean monthly range of 5 °C (Fig. 2).
As evidenced from protected areas like churches and grave yards, climatic–climax vegetation found in the area include Juniperus procera (locally tid), Hagenia abyssinica (locally called kosso); Albizia gummifera (Sassa); Podocarpus falcatus (Zigba); Cordia africana (wanza); and Ficus vasta (Warka). Field observation also indicated that non-indigenous tree species like Cupressocyparis leylandii (yeferenj Tid), Acacia sieberiana (Yefereng Girar) and Eucalyptus spp. (Bahir zaf) are expanding.
Subsistence rainfed crop production with supplementary traditional irrigation and livestock husbandry are the main sources of livelihood. Dera wereda ARD office (2013) showed that the commonly grown crops in the catchment include barley (Hordeum vulgare L.), maize (Zea mays L.), teff (Eragrotis teff), noug (Guizotia abyssinica), and finger millet (Eleusin coracana).
Data sources and methods of analysis
Time series black-and-white photographic and Landsat satellite images were the main source of input data for the LULC analysis in this study. The 1957 aerial photographic images and 1973 Landsat image were the only oldest remote sensing data available for the study area, but there were no any reference images available between 1957 and 1973. Thus, further subdivisions for LULC analysis between 1957 and 1973 were not possible. Eleven 1 m × 1 m black-and-white scanned photographic images of 1957 by 600 dots per inch (DPI) were obtained from Ethiopian Mapping Agency (EMA). These were used for photogrammetric processing, as well as visual photo-interpretation activities. Materials such as mirror and pocket stereoscopes were employed for stereo viewing during visual interpretations of features on hardcopy pairs of aerial photos. The visual interpretations process using stereoscopes were helpful to substantiate onscreen feature classifications using GIS environment. Subsequently, all photographic images were geometrically corrected based on geo-referenced and 1:50,000 scale topographic map to produce orthorectified images using “Geo Correction Tools” of ArcGIS. Finally, the mosaic image was produced from eleven orthorectified images using “Mosaic Tool” and later “subset image” into the required study area AOI of ERDAS EMAGINE 9.2.
Landsat images were downloaded from Global Land Cover Facility (GLCF) in the USGS archives at Glovis (http://glovis.usgs.gov). Five images were downloaded at about ten years’ interval to easily visualize changes in spatiotemporal LULC patterns. However, some discrepancy ±1 year was considered due to the availability and quality of Landsat images from USGS archives for the study area. Therefore, the Landsat MSS of 1973 (60 m × 60 m), Landsat TM of 1984 and 1995 (30 m × 30 m), Landsat ETM+ of 2004 (30 m × 30 m) and Landsat OLI of 2014 (30 m × 30 m) at path (169 and 170p), and row (52r) images were used. These were preprocessed such as layer stacking, sub-sampling the study area by AOI file, re-sampling of all time-series images into similar ground resolution (30 m × 30 m), gap filling for Landsat 7 SCL-off (2004 and 2014 images), and spectrally enhancing the images before actual image classification process.
The major LULC classes considered in the classification are as given in Table 2. The farm and settlement areas were included in the same land cover as it was difficult to separate these two on the employed images. Likewise, wetland class has been excluded in the classification process as an independent LULC class because this class largely covered with grassland, cultivated fields and forest adjacent to Lake Tana. Consequently, it was difficult to analyze wetlands separately while the area under study is occupied by different LULC classes. About 100 ground control points (GCP) representative of the different LULC classes were taken by a GPS receiver to improve accuracy of classification and to produce thematic land cover maps representative to the entire study period. Field observation was also conducted to substantiate the image classification and analysis.
LULC classification was based on quantitative method that requires an independent classification of time-series images for the same geographic location followed by a comparison of the corresponding pixels to identify and quantify areas of change (Lillesand and Kiefer 1994). Based on the correlation between the collected field data and the preliminary visual interpretation, the entire area was delineated from the orthorectified and geometrically corrected historical aerial photographs of 1957 using on-screen digitization by “Spatial Analysis Tool” of ArcGIS 10. The digitized vector data also have undergone editing, overlay analysis and topological checks. Finally, cartographically finished historical LULC maps of 1957 were produced. Conversely, because of low resolution of Landsat images, only major LULC types were considered. Accordingly, supervised classification was done using training areas obtained from ground truth data combined with spectral signatures in false color composite images by maximum likelihood classifier. Subsequently, the accuracy assessment was conducted for all the classified Landsat images (maps) using accuracy assessment tool in ERDAS Imagine 9.2 to evaluate the user’s and the producer’s accuracy. Thus, the accuracy assessment result indicated that most of the maps met the required minimum 85% accuracy in LULC analysis as reported in Table 1. This showed a strong agreement between the classified LULC classes and the geographical data (ground truths) and made it possible to use the output maps for change detection analysis.
Once image classifications and accuracy assessment have been completed, six different LULC maps have been produced one in vector format (1957) and the rest in raster format (between 1973 and 2014) where calculation of the area in hectare, comparison of the LULC statistics within and between classes, and years were made possible (Table 2). As a result, the rates of change of LULC classes were determined in terms of percentage by:
where At1 is the area of one type of land use in t1 time; At2 is the area of the same type in t2 time and C is the rate of change in percent. This formula is a simple and effective method of weighting the relative rate of change of one LULC class over time where the change directions are determined. Moreover, matrix analyses (image differencing) were employed for images between 1973 and 1995, 1995 and 2004, 2004 and 2014 to determine the LULC change detection using change detection tool in ERDAS Imagine 9.2. However, change detection between 1957 and 1973 was not possible due to incompatibility of 1957 LULC map in the change detection analysis of ERDAS Imagine 9.2. Accordingly, areas that are converted from each LULC class to any of the other over time were computed. The change detection matrix represented the simultaneous gross loss and gain for each LULC class where net losses or gains could be calculated in a given period of analysis. However, field observation and informal interview with the local elders using observation checklist and interview guide were also undertaken in the study area to substantiate the information obtained from GIS and remote sensing based LULC analysis. Therefore, LULC analysis was done using ERDAS Imagine 9.2 and ArcGIS 10 version involved key steps (Fig. 3).
Results and discussion
LULC change in the study catchment between 1957 and 1973
Table 4 and Fig. 4 indicated an existence of spatiotemporal transformations in the identified LULC classes. Shrinkage of forest cover was observed between 1957 and 1973, while the other LULC classes showed expansions of their original extent in this early period of analysis. Forest cover was declined by 71.5% (265.2 ha/year) over the time span of 16 years. The shrinkage could be attributed to destruction of natural forests in search for additional farm plots, construction materials and domestic fuel consumption in the study catchment. However, farmland and settlement cover, which accounted the lowest coverage ever in the entire 57 years, but has been extended by 12.9% (73.3 ha/year). Shrubs accounted for 27% of the total area of the catchment in 1957 and expanded by 10.2% (45.5 ha/year). Likewise, grasslands were around 15.8% of the study area and exceptionally increased by 51.7% (134.2 ha/year). These possibly reflect the impacts of deforestations on land use transitions where natural forests are ultimately converted into farmlands, shrubs and grasslands between 1957 and 1973. Actual transformed figures of LULC class to other were not given because change detection matrix analysis was not possible.
LULC change in the study catchment between 1973 and 1984
An expansion of farmland and settlement, forests and bare land were observed between 1973 and 1984 (Table 4). The change detection matrix also indicated similar results although some portions of their original extent were converted into other LULC classes (Table 5). The farmland extended by about 19.24% (1961.51 ha), giving an annual average expansion of 178 ha/year. The expansion was largely contributed by shrubs by about 32.3% (3946.1 ha) and grassland by about 15.8% (1929.56 ha) despite some of the original extent was converted largely into grassland by 16.9% (1735.59 ha), and shrubs by 26.04% (2660.21 ha). This indicated farmlands were expanded, largely, at the expenses of shrubs and grasslands as the only means of increasing crop production. This expansion could also be attributed to the demand for attaining of food crops and more settlement land (Fig. 5). This suggests that food crop production under the then period of Ethiopian situation could have been obtained through farmland expansions; which is a sign of poor land productivity as well as leading to destruction and farming of non-cultivated lands such as grazing, shrubs and wetlands.
The exceptional increment of forests by 20.06% (338.87 ha) was largely due to additional areas obtained from grassland by 13.7% (277.56 ha), farmland and settlement by 18.7% (379.82 ha), and shrubs by 37.75% (765.94 ha) despite some of the original cover was lost largely into farmland and settlement by 52.98% (895.27 ha) and shrubs by 6.97% (117 ha). This suggests that land acquisition from other LULC classes for forest conservation program was in response to initiatives of restoring indigenous trees and forests by the past socialist regime’s forest development program since the establishment of Gelda protected forest in 1980. Similarly, bare land cover also expanded due to major area gain from conversion of grasslands by about 59.2% (119.6 ha), and farmland and settlement by about 29.3% (59.35). The expansion of bare land reflected the impact of unsustainable utilizations of grasslands and farmlands due to overgrazing and land degradation.
Shrinkages were observed in the extent of grasslands by 27.6% (158 ha/year) and shrubs 7.26% (52 ha/year) despite some gains were obtained from other LULC classes (Table 4 and 5). It is because some areas gained areas from different LULC classes could not bring a net expansion in grasslands and shrubs or did not compensate its decline in this second period of analysis. The substantial decline for grasslands were largely contributed by conversion of its original extent into farmland and settlement 30.63% (1929.56 ha) and shrubs by 33.92% (2136.44 ha) despite some gains were observed mainly from farmland and settlement by 38% (1735.59 ha) and shrubs by 19.2% (875.56 ha). This was attributed to land acquisition for farmlands following the downfall of the imperial regime in 1974 and the resulting policy changes at the expense of grazing lands and shrubs. This also showed the increasing demand for farmlands as well as forest development into areas once occupied by grassland. In addition, shrinkage of shrubs were largely due to conversion of its original extent into farmlands and settlement by about 50.2% (3946.1 ha) despite some area gains were observed mainly from grasslands, and farmland and settlement by about 29.3% (2136.44 ha) and 36.48% (2660.21 ha), respectively. This clearly showed that about half of the original shrubland were transformed into farmland and settlement caused by population pressure and changes in land tenure system that transformed landless tenants into land owners.
LULC change in the study catchment between 1984 and 1995
LULC study between 1984 and 1995 showed expansion of grassland, farmland and settlement, and bare land despite some area were lost into other LULC classes (Tables 4, 6). The area devoted to farmland and settlement showed a steady expansion by about 33.44% (370.3 ha/year) in this third period of analysis. Change detection matrix also indicated that the most important contributors of farmlands and settlement expansions were grasslands by about 11.93% (1940.02 ha) and shrubs by about 24.15% (3925.9 ha) despite some of its initial extent was transformed into other LULC classes (Table 6). This indicated that expansions were at the expenses of grasslands and shrubs cover. A remarkable expansions were also observed in bare land by about 89% (16 ha/year) and grasslands by about 28.67% (118.9 ha/year). The expansion of bare land was due to area gain obtained largely from grasslands by about 48.27% (183.85 ha). This showed that unsustainable grassland management in the form of uncontrolled grazing attributed to the transformations of its initial grassland cover into bare soil areas. As a result, expansions in grasslands were observed largely due to farmland and settlement by about 28.6% (1680.4 ha), and shrubs by about 33.66% (1975.4 ha) despite some its initial extent was mainly converted into farmland and settlement. This possibly forced the local farmers to prepare grasslands meant for grazing converted largely from their farmlands and shrubs.
Shrinkages were evident in forest cover 52.6% (97 ha/year) and shrubs 61.63% (408.6 ha/year) despite some area gains were observed from other LULC classes (Tables 4, 6). It was because the area gained from other LULC classes could not satisfy the losses or conversions from their original extent. The dominant reasons that largely contributed to the reduction of forest cover were conversion of its initial extent into farmlands and settlement by about 47.37% (960.98 ha), and shrubs by about 19.26% (390.8 ha) despite some gains from farmland and settlement. It was partly attributed to forced resettlement program between 1987 and 1991. This could be due to forest clearing in search for additional farmlands and new settlement units in socialist regime, particularly during rural resettlement program. The demand for local construction material and fuel wood, and civil war between 1990 and 1991 were the other reasons for forestland decrease. Shrubs have also been diminished as a result of conversion of its initial extent largely into grasslands by about 27% (1975.4 ha) and farmland and settlement by about 53.8% (3925.9 ha) despite some gains in farmland and settlement. It was partly related to political instability and change of political structure of the country, which led to the clearance of shrubs for expansion of farmlands and new settlement centers. These revealed that further vegetation clearance in search for additional farmlands, new settlement units and grazing could eventually transform the initial extents of shrubs.
LULC change in the study catchment between 1995 and 2004
The area under forests, shrubs and grazing lands has been expanded by about 29.51% (31.58 ha/year), 4.11% (12.8 ha/year) and 35.16% (229.3 ha/year) although some portions of their initial extent were converted into other LULC classes, respectively (Tables 4, 7). In this study period, expansion of grasslands was dominantly attributed to conversions of farmland and settlement by about 52% (4125.97 ha) despite some of the initial extent was largely converted into farmlands and settlement by about 31.2% (1834.12 ha). It was possibly due to land restoration that were illegally encroached by local community following the political vacuum since early 1990s. The forest cover has also been expanded mainly due to area gains from shrubs by about 28.4% (354.97 ha), and farmland and settlement by about 28.2% (351.86 ha) despite some portions of the initial extent of was simultaneously converted mainly into farmland and settlement. Similarly, the expansions of shrubs were largely contributed by farmlands and settlement by about 37.7% (1097.79 ha), and grasslands by about 25.7% (749.4 ha) despite some of the initial extents were converted mainly into farmland and settlement, grasslands, and forest cover by about 32.96% (922.61 ha), 17.6% (493 ha), and 12.7% (354.5 ha), respectively. This could be the collapse of the newly established villages following the downfall of the socialist regime and vegetation regeneration in areas that were under intense pressure by local community.
Table 7 also revealed that reductions were observed in farmland and settlement, and bare land because the added areas from other LULC classes could not be adequate to compensate the losses. Exceptional shrinkage was observed in farmland and settlement cover by about 14.6% (263.78 ha/year) possibly due to tough measures taken by the government to restore areas which were under forests, shrubs, grazing lands and those farmlands not suitable for agriculture (Table 4). The dominant contributors of the existing decline in farmland and settlement was associated with the conversions of its initial extent into grasslands by about 25.4% (4125.97 ha) and shrubs by about 6.7% (1097.79 ha) despite some area was largely gained from grasslands (Table 7). The areas previously occupied by farmlands and villages were declined following refusal of forced settlement and inadequate reaction from the transitional government in early 1990s. However, tough measures on land restoration were taken at the end of this study period that substantially reduced areas occupied by farmlands. Despite the fact that bare land constituted a very small spatial extent in the watershed, its original extent was decreased as much as 24.9% at the rate of 10.5 ha/year (Table 4). The decline was contributed mainly by the conversion of the initial extent into grasslands by about 54.8% (208.8 ha). This indicated that once the area is out of production and physically unsuitable for either of human uses, the area were exempted from any human contact and eventually recovered largely into grasslands.
LULC change in the study catchment between 2004 and 2014
Tables 4 and 8 revealed that the highest rate of expansion was observed in shrubs by about 190.35% (555 ha/year) followed by bare land by about 126.7% (36 ha/year), and farmland and settlement by about 2.72% (38 ha/year) despite some of their original extent was largely converted into other LULC classes. In this last period of analysis, the expansion of farmland and settlement was observed due to areas mainly gained from shrubs by about 6.5% (924.75 ha) and grasslands by about 22.8% (3259.98 ha) although some of the initial extent of has been largely converted into shrubs by about 25.5% (3534.84 ha). This lowest rate of increment was reflected in the expansion of eucalyptus and other trees planted at household level around homesteads, development of area closure, and other conservation measures in the study catchment. The Amhara region land reform with the premise of redistributing the land among farmers driven by population pressure and social injustice was also possibly attributed to farmland expansion at the expense of other LULC classes. Similarly, shrubs has been expanded largely due to areas gained from farmland and settlement by about 41.8% (3534.84 ha), and grasslands by about 39.9% (3377.97 ha) despite some of its initial extent was converted into farmlands and settlement by about 31.7% (924.75 ha). This could be the results of recent attempts of area closure and forest restoration, which subsequently transformed into shrubs. However, expansion in bare land was largely due to area gained from grasslands by about 57.5% (372.78 ha), and farmland and settlement by about 34.6% (224.46 ha). This could be the impacts of poor farmland practices and overgrazing.
Slight decline was observed in forest cover by 23.1% (28.8 ha/y) while the highest was in grazing lands by 75.65% (600 ha/year) between 2004 and 2014 (Table 4). These shrinkages were evident because some areas gained from other LULC classes were not adequate to compensate the losses from their initial extent (Table 8). Decline in forest cover was largely attributed to its conversion into farmland and settlement by about 43.5% (543.3 ha) and shrubs by about 8.5% (106.4 ha) despite some area gain from the classes of shrubs by 10.7% (102.6 ha), and farmland and settlement by 26.1% (250 ha). In this study period, various levels of vegetation clearance in search for farmlands and household consumption have possibly transformed the original forest cover into farmlands and shrubs. Similarly, reduction in grassland covers were mostly caused by conversion of its initial extent into shrubs by about 42% (3377.97 ha), and farmland and settlement by about 41.1% (3259.98 ha) despite some gains from other LULC classes. This was possibly associated to land encroachment for agriculture and land restoration which was not suitable for grazing into shrubs.
LULC change in the study catchment between 1957 and 2014
Table 9 demonstrated that shrubs, farmlands, and bare lands were expanded while grassland and forest cover were contracted over the past 57 years in the study area. Despite the forest plantation and conservation effort since 1980 in the catchment, forest cover has declined by about 83.83% (87.2 ha/year). It is because of the small success achieved by the government to fully cover the areas that were under poor management and exhaustively used. Although areas under grazing lands showed an irregular pattern of spatiotemporal variations, it has shown a decline by about 53.46% (38.9 ha/year) over the entire study period. However, the patterns of changes in areas under shrubs indicated that it has shown an expansion by about 18.6% (23.3 ha/year), which was partly attributed to the impacts of planting trees for household consumption around homesteads by local community; and recent campaign in soil and water conservation activities since 2011. The area under bare land contained less than 3% of the total area of the catchment; however the trend in its area showed that it has exceptionally expanded by about 11.37 ha/year. Farmland and settlement was expanded by about 57.68% (91.5 ha/year). This highest trend of expansion in bare land suggests the presence of unsustainable land management practices while farmland expansion was largely at the expenses of the natural forest cover and grasslands.
Major drivers of land use and cover dynamics
The LULC dynamics in the study area largely depend on dynamic relationships among population and policy/institutional factors, but the effect of natural factors such as climate over small area and short periods of time may not felt as such.
Although the overall demographic data for the study catchment was not possible to obtain following catchment boundaries, the data were compiled according to administrative structure where the catchment is almost entirely found. The demographic data were limited to three census reports of Ethiopia in 1984, 1994 and 2007; but LULC analyses were between 1957 and 2014. Thus, demographic data were used to see trends of population changes in the study area over larger portion of the study period so that comparison can be made possible among LULC change and population pressure. The data indicated that the total population of Dera wereda was increased from 204,962 in 1984; 212,341 in 1994 to 248,464 in 2007 at an average annual growth rate of 3.6 and 16.9% respectively (CSA 1991, 1995, 2008). This revealed that population pressure on the land resources increased the demand for farmlands, settlements, fuel wood, and construction materials. The census reports also indicated that most of the total population in the were da (>90%) resides in the rural areas where households largely depend on land resources as means of livelihood. This caused expansion of farmlands into shrubs, forests and grasslands; overgrazing; deforestation for household energy consumption and income; and declined arable land percapita in rural areas. These suggest that population growth is a major driving force in LULC dynamics of Gelda catchment. This is consistent with the previous studies in the highlands of Ethiopia (Woldeamlak 2002; Wubalem 2012; Hurni 1988; Mekuria 2005; Tsehaye and Mohammed 2015; Hassen et al. 2015). However, direct field observation and informal interview indicated that the scarcity of forest products for household consumption forced the local population to plant trees around homesteads and protect forests in areas not usable for agriculture in recent times. The expansion of farmlands and bare land in the study area were presumably attributed to the impacts of population pressure mainly in search of additional farmlands, overgrazing and poor farming practices. Sociopolitical influences, especially inse-curity of land tenure; disincentives among farmers for conservation programs; taking some land out of production and placing more pressure on existing farm and grasslands have discouraged farmers from investing in soil conservation practices since 1984 in the study area.
Institutional and policy factors
Ethiopia has undertaken many institutional and policy changes regarding land resources management following major changes in political and government structures in 1974, 1974 and 1991. These frequent changes in political and government structures were responsible for successive changes in land resource use and administrative frameworks in Ethiopia, which intern resulted in successive LULC changes in the study area. The major institutional and policy factors responsible for changes in LULC change were the downfall of the imperial regime followed by land reform of 1975 where farmlands were given to landless tenants confiscated from landlords, and clearing forest and shrubs. The forest restoration and plantations program of socialist regime since early 1980s using food-for-work program was another policy factor where success to date is rare due to lower local community involvement. The resettlement program between 1987 and 1990; civil war between 1990 and 1991; downfall of socialist regime; and the resulting legal vacuum in natural resource conservation attributed to the clearance of shrubs and forest cover. The 1997 land redistribution in Amhara region that aimed at ensuring social justice and responding to population change was another factor despite its failure to fully satisfy the ever increasing demand for farmlands and settlement.
There have been substantial LULC changes in Gelda catchment of northwestern highlands of Ethiopia driven mainly by population pressure institutional and policy factors. The existing expansions of traditional farming practices into grasslands, natural vegetations and marginal lands eventually led to a decrease in fodder availability and gradual soil quality deterioration. The decline in grassland forced the local community to keep their cattle on bare lands and shrubs, particularly during the cropping season. The institutional and policy reforms over the entire study period have contributed to changes the legal and policy frameworks of land resource management and ownerships in the country. These changes could have implications for sustainable agricultural resource management and the livelihood of the local community. As a result, off-farm activities and soil fertility improvement are essential to reduce the adverse impacts of population pressure on natural resource base. Improved land management practices such as applying soil and water conservation techniques and improved agricultural inputs could improve agricultural production. Likewise, local involvement in natural resource management and the existence of clear land tenure policies are critical for sustainable land use. Alternative energy sources for household energy consumption and environmental education are also imperative. Therefore, the change detection matrix analysis in GIS and remote sensing could provide useful baseline information to understand the spatiotemporal patterns of land use transitions and major contributors of LULC change caused by the major driving forces thereby sustainable land management planning is possible.
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EEH has conceived of the study. He has also participated in the design of the study, carried out the data collection, GIS and remote sensing based analysis of data, and performed the statistical analysis. MA has participated in the sequence alignment of the draft manuscript. He also participated in its design and coordination, and helped to draft and edits the manuscript. All authors read and approved the final manuscript.
The authors are grateful to Addis Ababa University (Addis Ababa, Ethiopia) and University of Gondar (Gondar, Ethiopia) for their financial and operational support to conduct this research. This study was also made possible by a research grant awarded to the first author by Association of African Universities (Accra, Ghana).We also thank the local farmers in the study area for their cooperation and understanding during field work. The paper has been benefited largely from anonymous reviewers.
The authors declare that they have no competing interests.
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Hassen, E.E., Assen, M. Land use/cover dynamics and its drivers in Gelda catchment, Lake Tana watershed, Ethiopia. Environ Syst Res 6, 4 (2018). https://doi.org/10.1186/s40068-017-0081-x
- LULC change
- Population pressure
- Driving forces
- Remote sensing
- Change detection