The Emergence of Irrigated Agriculture in Semi-Arid Zones in the Face of Climate Change and Urbanization in Peri-Urban Areas in Setif, Algeria
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1. Introduction
Consequently, this exerts mounting pressure on real estate resources, which are earmarked for urban development at the expense of agricultural lands. This creates a complex equilibrium equation within the geographical realm, entailing a trinity of urbanization, arable land, and groundwater, each of which demands careful consideration and management to ensure a harmonious coexistence.
The Algerian natural space, particularly the agricultural one, has become a subject of multiple pressures resulting from human activities, including agricultural production and urbanization. These activities have been a subject of controversy among local farmers, investors, and urban operators. As a consequence, agricultural spaces have gradually undergone a process of “artificialization” due to rapid urbanization.
In addition to these factors, climate change and the perceived temperature rise have further exacerbated the ecosystem of the Sétif urban area, leading to large-scale wildfires in recent years, particularly in 2021 and 2022. This phenomenon raises questions about the need to revise agricultural practices and adopt new methods in the study area, despite the historical predominance of traditional agro-pastoral practices.
Figure 1.
Perpetual duality between structural elements and the environment.
Figure 1.
Perpetual duality between structural elements and the environment.
The main objectives of this research are, firstly, to analyze the introduction, and then to analyze the temporal and spatial dynamics of irrigated crops in the study area. This diachronic and geographical approach will contribute to the understanding of agricultural transitions. Additionally, this study aims to explain the reasons behind the emergence of these crops in a semi-arid zone that was historically characterized by cereal farming, resulting in low to moderate annual yields due to erratic rainfall.
The crucial aspect of this research also involves measuring the impacts of irrigated crops on the local water table. By evaluating the underground water level drawdown, we aim to determine the environmental implications of irrigation on water resource availability, as well as the long-term sustainability of these practices.
This notably involves assessing the potential impact on crop diversification and resilience to climate change. By closely examining these aspects, we aim to provide insights to guide future agricultural practices in similar semi-arid areas.
Finally, the overarching objective of this study is to reach a consensus on the future use of peri-urban space, considering the evolution of agricultural and urban practices. This process aims to strive for the sustainable utilization of space by taking into account the food needs, environmental requirements, and urban development imperatives in the study area.
2. Study Area
Naturally confined between Mount Mokrass at 1737 m to the north and the Harraanah Mountains to the south, represented by Mount Boutalib, which soars to an elevation of 1886 m (the summit of Afrajane), the study area stretches across a wide plain with an average elevation of 950 m above sea level. This region is characterized by dispersed and detached mountain masses, appearing sporadically, such as Mount Youssef at 1442 m. Moreover, the area is punctuated by marshes and saline depressions, including the Mullah Marsh, Al-Hamiyat Salt Flat, and the Meloul Salt Flat.
The soil in the area is diverse, offering opportunities for agricultural activity. It consists mainly of continental deposits dating back to the Pliocene and Pleistocene periods, characterized by their lack of cohesion due to the presence of sandy silt and clay. The extensive limestone areas also provide significant opportunities for groundwater presence due to their higher permeability. Furthermore, the soils of recent deposits, especially along valleys, are of good quality and gray in color, while the remaining high plateau lands are characterized by limestone soils.
The study area features a semi-arid continental climate resulting from its central location between the Tellian and Saharan mountain ranges, characterized by hot and dry summers and cold winters. The precipitation regime is semi-arid, ranging from 200 mm to 400 mm per year with fluctuations, impacting agricultural yields, especially for cereal crops, and affecting human behavior, leading to recurrent shortages of certain food products.
Historically, the local population practiced cereal cultivation and sheep farming, which are activities that have been adapted to the climatic conditions of the study area, while irrigated plots were very limited. The introduction of irrigated cultures is a recent development. Following this presentation, it becomes apparent that various natural and geographical factors (excluding soil nature) do not favor the irrigated agriculture model. However, in recent years, there has been some expansion of this type of agriculture. All of these factors have contributed to directing our choice towards this area to study the new trend in agricultural exploitation models and their effects on the environmental balance of the area.
4. Results and Discussion
4.1. Climate Changes in the Study Area Are Trending towards Acidification
4.2. Urban Changes in the Study Area in Response to Population Pressure
4.3. Peri-Urban Agriculture
In this study, we relied on pixels with values ranging from 0.4 to 0.8 to accurately determine the vegetative cover, especially densely cultivated areas that are irrigated in the summer. This is due to the region’s semi-arid nature, where green areas are generally absent during the summer, except for forested areas or irrigated crops. Harvesting is typically complete, as the primary agricultural activity in the region has traditionally been cereal cultivation, as previously mentioned.
As previously noted, the region has historically been renowned for cereal cultivation. However, two key factors have contributed to this shift. First, the region has experienced climate changes, resulting in decreased precipitation, which was the primary source of support for cereal cultivation. Second, the expansion of urban areas due to population growth has significantly increased the demand for food, particularly the products of intensive agriculture, such as tomatoes, peppers, beetroots, salad, and carrots.
A noteworthy observation that is equally important is the proliferation of poultry farming in the southern part of the study region. Extensive areas and livestock stables for poultry and cattle have been observed on lands previously allocated for cereal crops. This reflects farmers’ attempts to compensate for the decline in income from cereal cultivation.
4.4. Remarkable Evolution of Demographic and Agricultural Indicators in the Study Area during the Study Period (2000–2020)
Table 3.
Evolution of population, irrigated lands, and horticultural production in the study area between 2000 and 2020.
Table 3.
Evolution of population, irrigated lands, and horticultural production in the study area between 2000 and 2020.
Variables/Time | 2000 | 2010 | 2020 | 2000–2010 (%) | 2010–2020 (%) | 2000–2020 (%) |
---|---|---|---|---|---|---|
Population * | 447,529 | 525,424 | 671,132 | 17.40 | 27.73 | 49.96 |
Area of irrigated land (hectare) ** | 5951 | 8581 | 8653 | 44.19 | 0.83 | 44.19 |
Horticultural production (quintal) ** | 239,179 | 500,205 | 747,391 | 109.13 | 49.41 | 212.48 |
Furthermore, the area of irrigated land also substantially increased between 2000 and 2020, expanding from 5951hectares in 2000 to 8653hectares in 2020, marking a growth of 44.19% during the same period. This expansion of irrigated land not only demonstrates increased investment in water resources (through drilling) but also contributes to the depletion of the groundwater as a consequence.
However, during the period from 2010 to 2020, the irrigated area experienced stability primarily due to a decrease in precipitation volumes during the same period, which could not ensure sufficient groundwater replenishment.
It is important to highlight that a significant number of farmers exploiting these lands are not the actual owners of the agricultural land. They come from neighboring regions and choose to lease these lands. Their primary motivations are immediate profit and short-term financial returns. In this context, they often fail to consider the implications of the excessive exploitation of groundwater in the long term. This dynamic highlights a form of natural resource exploitation that lacks rationality in the study area.
4.5. Substantial Growth in Protected Crop Cultivation (Plastic Greenhouses)
Table 4.
The evolution of protected crops in the study area during the study period (2000–2020).
Table 4.
The evolution of protected crops in the study area during the study period (2000–2020).
Variables/Time | 2000 | 2010 | 2020 | 2000–2010% | 2010–2020% | 2000–2020% |
---|---|---|---|---|---|---|
Protected Area (H) | 19.88 | 78.62 | 405.89 | 295.47 | 416.26 | 1941.70 |
Production (QX) | 9310 | 43,041 | 455,455 | 362.30 | 958.188 | 4792.10 |
In conclusion, this observation underscores the crucial importance of the sustainable and effective management of natural resources to meet the growing population’s demands. It is essential to remain vigilant in the face of these trends and adjust development policies to ensure a balance between the increasing needs of the population and the groundwater resources of the study area, as extraction rates exceed the recharge of the aquifer.
4.6. Excessive Exploitation of Underground Water Levels
This can be explained by two main indicators. The first indicator is climate change, resulting from decreased precipitation and an increased demand for groundwater resources, particularly in intensive summer agriculture.
The second factor is the demand arising from urban expansion and associated human activities. With the continued phenomenon of drought and reduced precipitation, almost all wells have dried up completely or nearly so (four out of five wells). This has prompted investors to seek permission from the Administrative and Technical Authority for Groundwater Resources to drill deeper wells, reaching depths of up to −350 m in certain areas, such as Ain Oulman. This situation reflects a state of groundwater depletion in the study area and creates difficulties in restoring balance to groundwater levels, especially given the non-harmonious hydrogeological structure of the region.
5. Conclusions
The relationship between urban populations and the natural environment remains a vital and fragile issue, as ensuring a comprehensive balance among the environmental elements in which they reside, especially between urban expansion and neighboring farmlands, proves to be challenging. This duality has long been based on a struggle for control over one another.
The studied area (the peri-urban zone of Setif) has known significant transformations in the past twenty years (2000–2020), with the most prominent being the significant rate of population growth. Their number shifted from 447,529 in 2000 to 671,132 in 2020, representing an increase of approximately 49%. Consequently, the city of Setif, along with its peri-urban area, transformed into a regional metropolis. This human weight produced a shift in agricultural patterns by introducing intensive agriculture. The irrigated agricultural areas increased by 44.19% between 2000 and 2020, leading to a 212.4% rise in vegetable production during the same period. Additionally, a qualitative evolution occurred with the emergence of protected agriculture using plastic greenhouses, expanding from 19.88 hectares in 2000 to 405.89 hectares in 2020 (an increase of 20 times in area). All of these transformations took place in a region that was previously characterized by grain cultivation and ranching. In contrast to these significant changes, the underground water level has shifted from a depth of −50 m to −150 m in the northern study area. In the south, the water depth has reached −300 m.
This new pattern—irrigated and protected agriculture—is unintended and undefined in the state’s major goals and directions. This the result of automatic, individual, and collective choices made by official and unofficial actors aiming to earn quick profits. This pattern remains unknown in its consequences, in a changing climate characterized by periods of drought, fluctuating and decreasing precipitation, alongside a decline in underground water levels in the study area. Consequently, the water in the study area will not comply with the new direction of agriculture, which leans towards depleting local groundwater. This faces a challenge due to insufficient precipitation. Thus, it requires diverting water from the more rainfall-abundant northern coastal regions to the semi-arid inland areas as a first step. However, in our opinion, it is necessary to explore the process of desalinating seawater (100 km away) to meet the water demands of both the population and agriculture simultaneously.
Finally, in order to ensure a new equilibrium between population, urban growth, and agriculture in peri-urban areas, especially in semi-arid regions, it is necessary to incorporate the issue of food into the planning programs and local and regional development tools in the future. This is especially crucial as the state continues to respond to social housing needs in an urgent manner at the expense of agricultural land. Additionally, there is a haphazard exploitation of underground water, leading to situations that open up another area of research into how to manage underground water in the region and protect the environment in semi-arid areas amidst climate change. Also, it is possible to direct future attention towards the comprehensive study and analysis of the relationship between these variables in a deeper and partial manner, aiming ultimately to develop interpretations that assist in making more realistic decisions.
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