Umer Abdela- Department of Environmental Science, Madda Walabu University, Bale Robe, Ethiopia
Pastoral communities in Ethiopia’s Bale Zone face a constant threat: drought. The Bale lowlands are Particularly vulnerable due to unpredictable rainfall patterns. A 4-year drought cycle had gripped the region, as reported by the pastoralists themselves. Rising temperatures and declining rainfall painted a concerning picture, leading to a cascade of problems: crop failures, food insecurity, outbreaks of diseases, and increased child school dropout rates. This in-depth study aimed to shed light on the impact of drought on these communities and their remarkable capacity to adapt. By bridging the knowledge gap on drought’s influence and local coping mechanisms, the study hoped to inform future interventions. The objectives were to identify the impact of drought on Bale’s pastoral communities and to identify the coping mechanisms employed by these communities. The study utilized a mixed-methods approach to capture both qualitative and quantitative data. Data collection techniques included: Engaging with knowledgeable community leaders provided valuable insights into historical trends, community perceptions, and local decision-making processes, Facilitating group discussions allowed community members to share their experiences, concerns, and coping mechanisms in a collaborative setting and administering standardized surveys to a representative sample of households allowed for the quantification of drought’s impact and the prevalence of various adaptation strategies. The Results shows all study locations experienced drought for four consecutive years (100%), Pastoralists reported rising temperatures and declining rainfall. The drought resulted in, Crop failures, Food insecurity, Livestock deaths, increased human and livestock diseases increased child school dropout rates. The study concluded that despite the challenges, the study revealed a heartening story of resilience. Bale’s pastoral communities have not succumbed to despair. Instead, they have developed a multifaceted approach to cope with drought, including: Utilizing existing water sources and creating communal grazing areas for better water conservation, Splitting herds to reduce grazing pressure, implementing early morning grazing to capitalize on dew, diversifying livestock breeds, and strategically destocking herds before droughts to ensure long-term herd sustainability, Diversifying income through trade, transportation services, and petty trade to reduce dependence on livestock production during droughts. Leveraging the enduring strength of traditional social safety nets (“hirpa,” “dare,” and “hameessa”) for crucial support and assistance during hardships. The study underscores the importance of supporting these existing strategies. Policymakers and NGOs can play a vital role by strengthening social safety nets, promoting the adoption of drought-resistant agricultural practices, investing in research on improved water management techniques and drought-resistant crop varieties.
1 Introduction
Droughts are a growing threat worldwide, becoming both more frequent and severe (Kogan et al., 2016). Considered as one of the deadliest natural disasters, droughts unleash a cascade of disaster including crop failures, food shortages that risk famines, malnutrition, health problems, and even mass migrations (IPCC, 2012). While developing countries are often considered more susceptible to droughts, history shows these events can be widespread and devastating (Glantz, 1994). The trend is towards more frequent and severe droughts, threatening even major grain producers like the US, China, and Europe (Kogan et al., 2016). Developing countries face a disproportionate burden and despite experiencing only 8% of global disasters particularly vulnerable to droughts (Sharma and Ravindranath, 2019, IPCC, 2012/14).
Droughts have a severe and multifaceted impact on developing countries, exacerbating poverty, food insecurity, and health issues (Tache, 2008; Amsale, 2010 and Funk et al., 2018). Agriculture, the backbone of many developing economies, suffers tremendously as crop yields plummet and livestock perish due to water scarcity (Bryan et al., 2013 and Funk et al., 2018). This results in significant income loss for rural communities heavily reliant on agriculture (Kurukulasuriya, and Rosenthal, 2013). The economic strain is further compounded by water scarcity, which not only impedes farming but also disrupts daily life and industrial activities, creating a ripple effect throughout the economy (Bessachi, and Announ, 2023). For instance, recurrent droughts in sub-Saharan Africa have led to chronic food shortages, forcing millions into malnutrition and driving up food prices (Bishop, and Dimoulias, 2024). Furthermore, the lack of clean water sources due to drought increases the risk of waterborne diseases, placing a burden on already fragile healthcare systems and contributing to higher mortality rates, particularly among children (Bishop, and Dimoulias, 2024). These factors combine to demonstrate that the impacts of drought in developing countries are complex and far-reaching, undermining development progress and exacerbating existing vulnerabilities (Manger, 2000).
Sub-Saharan Africa endures most of drought’s impact due to its large population reliant on rain-fed agriculture (IPCC, 2014; Masih et al., 2014). The Sahel region serves as a tragic example, experiencing exceptional drought since the 1960s (Mishra and Singh, 2010). This area, already stressed by climate challenges, has seen a particularly worrying rise in droughts since the late 1800s, with three major events causing severe environmental and socioeconomic damage (Gautam, 2006). Droughts are not limited to the sahel; regions like the greater horn and southern Africa are also highly vulnerable (Hansen et al., 2004; Gautam, 2006). These frequent and prolonged droughts impact communities at all levels, from households to entire nations, with Eastern Africa experiencing a rise in drought frequency compared to a slight decrease in West Africa over the past 50 years (Gautam, 2006).
The vulnerability stems from a combination of climatic factors such as lack of rainfall, hot temperatures, and increased evaporation that are often worsened by human activities like deforestation and overgrazing (Gautam, 2006; Abubakar and Yamusa, 2013; Adegboyega et al., 2016). Climate change further compounds these issues by shortening growing seasons and reducing yields and places even greater stress on livestock, a critical asset for many poor pastoral communities (UNFCCC, 2007; Fereja, 2016). Ethiopia has a long history of battling severe droughts with devastating consequences (Gebrehiwot et al., 2011; Alemayehu, 2023). The country has experienced over 30 major droughts, with some causing widespread death tolls and hardship (Melaku, 2013; Bayissa et al., 2017). The 2017 drought triggered by the Indian Ocean Dipole serves as a recent example (FAO, 2017). Ethiopia faces erratic weather patterns, including a concerning decline in rainfall during the crucial cropping season (Mertz et al., 2009). This erratic rainfall is linked to the country’s frequent and devastating droughts, which have caused famines since the 1960s (Alemayehu, 2023). The historical frequency of droughts is worsening, with occurrences potentially becoming annual events (Margaret, 2003; FAO, 2017; Bogale and Erena, 2022). Several factors exacerbate Ethiopia’s susceptibility to droughts, including unreliable rainfall, rising temperatures, persistent drought conditions, and the El Niño Southern Oscillation (ENSO) phenomenon (Goitom and Asefa, 2017; Worku and Sahile, 2018; Habte et al., 2022).
Climate change is a significant driver of these issues (Mogotsi et al., 2013; Weldegebriel and Prowse, 2013) while biophysical and social factors like poverty and resource depletion further worsen vulnerability (FAO, 2017; Goitom and Assefa, 2017; Mohammed et al., 2017). These factors create a vicious cycle when combined with droughts. Ethiopia’s heavy reliance on rain-fed agriculture makes it highly vulnerable to declining agricultural productivity due to rising temperatures and decreasing rainfall (Deressa et al., 2008; Temesgen, 2010; Blauhut, 2020; World Bank, 2020). This decline directly threatens food security in the country livestock, particularly cattle, are a critical source of income for Ethiopia (World Bank, 2020). However, climate change poses a significant threat to this sector by reducing livestock productivity (Yilma et al., 2009). Factors like lower quality and quantity of forage, increased diseases, and heat stress all contribute to this decline (Kefyalew and Tegegn, 2012; Gashaw et al., 2014; Hidosa and Guyo, 2017). Droughts, like other hydrological extremes, trigger a complex chain reaction of negative consequences. The “domino effect” aptly captures how a single event, like a drought, disrupts one sector and sets off a series of interconnected problems (income loss, food scarcity, instability) (de Brito, 2021). However, the “cascading hardships” concept goes a step further by highlighting the accumulating nature of these impacts. Each triggered event creates additional challenges, making the overall situation progressively worse over time (de Brito et al., 2024). Droughts in Bale zone trigger a series of negative consequences and reduced rainfall leads to land degradation, biodiversity loss, and overgrazing (BZPADO, 2022). This combination creates a domino effect where cumulative effect produced when one event sets off a series of similar or related events, a form of chain reaction (Wang and Weng, 2020), causing severe soil erosion, lowering the water table, drying out the soil, and damaging pastures (BZPADO, 2022). The result is crop failures, deaths among people and livestock, and even border conflicts for resource access (BZPADO, 2022). Droughts further exacerbate existing challenges by causing increased migration, disputes over boundaries, and outbreaks of diseases (BZPADO, 2022).
Ethiopia’s pastoral communities, heavily reliant on livestock, face the brunt of climate change (Scoones, 2004). Unfortunately, research suggests a decline in both the pastoral resource base and the customary institutions that govern them (Oba, 1998; Helland, 1998; Kamara, 2003; Boku, 2008). This weakening foundation threatens the very livelihood of these communities. These repeated droughts expose the critical issue of feed shortages in Bale’s pastoral districts (BZPADO, 2022). Research documented significant livestock deaths between 2016 and 2018, with problems persisting (Delbiso et al., 2018). Decades of drought have made some of Bale zone districts the most food-insecure in Ethiopia, reliant on aid programs like the productive Safety Net Programme (PSNP) (Belay et al., 2005; Foran et al., 2012).
The Ethiopian government acknowledges the country’s vulnerability to droughts due to climate change (Lemma, 2013). Furthermore, they recognize the need for more localized research on drought patterns and adaptation strategies specific to Bale’s pastoral communities (Lemma, 2013). Existing studies on climate change impacts, local adaptation options, and community response plans in these areas are limited (Sinay and Carter, 2020). This research gap highlights the importance of understanding how droughts affect these communities and the coping mechanisms they employ. Examining the consequences of droughts and potential adaptation strategies is crucial to inform policymakers and planners (BZPADO, 2022). Therefore, this research aimed to fill this gap and contribute by conducting assessment on community-driven drought risk management strategies in pastoral and agro-pastoral district of Bale zones southeast Ethiopia and the outcomes of this research are useful in similar study areas with similar challenges.
2 Research Methodology
2.1 Studyarea
Pastoral and agro-pastoral production systems are a cornerstone of life for a substantial portion of Ethiopia’s Oromia Regional State. These pastoral and agro-pastoral (PAP) systems are practiced across eight zones: Borana, Guji, West Guji, East Bale, Bale, East Showa, West Hararghe, and East Hararghe. Encompassing 43 districts, this vast area covers 152,070 square kilometers, which translates to 43% of the Oromia region’s landmass (OPADCC, 2019 unpublished). This territory stretches from Moyale in the Borana zone to Chinaksan in the East Hararghe zone. The predominant vegetation in Oromia’s pastoral areas is savanna-type grassland and bushland. This ecosystem provides sustenance for a variety of livestock, including cattle, camels, and small ruminants like goats and sheep. These pastoral lands are scattered across the southern, southeastern, and eastern parts of the Oromia region. Compared to other regions, Oromia’s pastoral communities tend to have a lower degree of livelihood diversification, meaning their income relies heavily on pastoral activities. These communities also have a lower level of market integration, suggesting they may sell or purchase fewer goods and services compared to other areas. The spread of invasive plants like Acacia drepanolobium presents a growing threat to herders’ livelihoods (Gebremeskel et al., 2019). It outcompetes native plants, reducing grazing land and forcing herders further for forage. This weakens the ecosystem and potentially reduces crop yields, creating a cycle of declining productivity and resource limitations. The pastoral areas within both Bale zones share these characteristics with other pastoral regions in Oromia and across Ethiopia (Figure 1). The chosen districts, Rayitu, Sawena, Gura Dhamole (pastoralist) and Lagahidah, Dalo mena, and Harena Buluk (agro-pastoralist), represent a variety of ecological zones, livelihood types, and factors that might arise during a drought or border conflict. By including these diverse locations, the investigation aims to gather well-rounded information applicable to a wider range of scenarios.
Figure 1. Location Map of Bale pastoral areas.
2.2 Sampling procedure and sample size determination
This research employs a multistage purposive sampling approach to ensure the collected data accurately reflects the realities faced by pastoralists in the Bale zones, particularly regarding the impact of recurring droughts on their livelihoods (Bernard, 2017). This approach prioritizes capturing in-depth data from the most relevant populations, even though it may not be statistically generalizable to the entire Bale zone population. In the first stage, six districts were chosen purposefully, considering two key factors such as livelihood type and drought severity considerations (Scoones, 2004). Accordingly, three agro-pastoralist districts (Lagahida, Dalo mena, and Harena Buluk) and three pastoralist districts (Rayitu, Sawena, and Gura Dhamole) were selected to ensure the survey captures the experiences of both groups who may have distinct vulnerabilities and adaptation strategies during droughts. In addition, Geographic representation, and the severity of recent drought conditions within the Bale zones influenced the selection of specific districts (Mutimba and Mortimore, 2005). Therefore, districts’ experiencing more frequent or intense droughts in recent years were prioritized to ensure the sample reflects a range of drought experiences and allows for exploration of potential variations in coping mechanisms across these diverse drought conditions.
In the second stage, two villages were purposefully chosen from each of the six selected districts. Like district selection based on drought prevalence, location, and accessibility villages with a documented history of frequent or severe droughts were prioritized consulting local reports on drought occurrences from Bale zone (Gebrehiwot et al., 2011). In addition, villages were chosen from geographically diverse locations within each district to ensure the research captures potential variations in drought impacts due to factors like microclimates or proximity to water sources (Desta and Hailemariam, 2010). Moreover, ease of access for conducting the household survey was also considered to ensure logistical feasibility (Bernard, 2017). A specific Yamane’s single population proportion formula was used to determine the final sample size of households for the survey (Yemane, 1967).
2.3 Data collection and analysis method
This research employed a mixed-methods approach to comprehensively assess community-driven drought risk management strategies in Bale zones’ pastoral and agro-pastoral districts. This approach combines quantitative and qualitative data collection methods to achieve a well-rounded understanding of the topic (Creswell and Plano Clark, 2018).
2.3.1 Data collection methods
For quantitative data collection Household Surveys were conducted. A representative sample of households across the study villages was selected using a stratified random sampling technique (Babbie, 2010). The questionnaire was developed based on existing literature on drought, drought early warning and adaptation strategy (Beyene and Kussa, 2018; Gebrehiwot et al., 2011) and pre-tested in the field to ensure clarity, cultural appropriateness, and internal consistency (De Vaus, 2002).
For qualitative data collection focus group discussions (FGDs) and Key Informant Interviews (KII) was employed. Focus group discussions were conducted in each village with purposefully selected participants from diverse demographics (age, gender, socio-economic status) within the pastoral and agro-pastoral communities (Morgan, 2019). A semi-structured discussion was used to facilitate discussions on community experiences with drought, early warning system, existing coping mechanisms, and challenges faced (Morgan, 2019). In addition, key informant interviews with semi-structured interviews were conducted with community leaders, elders, and development agents who possess in-depth knowledge of the region’s drought history, local adaptation practices, and social dynamics (Bernard, 2017). The interview focused on exploring topics such as community preparedness, effectiveness of existing strategies, and perceived impacts of drought on livelihoods (Bernard, 2017).
The research employed a set of questions themes to organize the data collection instruments (questionnaires, interview guides, FGD discussions) and guide the overall investigation of community-driven drought risk management strategies in the Bale zones. These questions’ themes encompass various aspects of drought experience and response within pastoral and agro-pastoral communities, sample questions were summarized in the following Table 1.
Table 1. Summerized questions used for the research (but not limited to the following).
2.3.2 Data analysis
The collected quantitative survey data was entered and cleaned in a statistical software program (SPSS). Descriptive statistics (frequencies, percentages) were used to summarize the prevalence of different adaptation practices across the study population (Field, 2018). For qualitative data analysis from KIIs and FGDs was used in narrative analysis to capture the lived experiences and perspectives of participants regarding drought adaptation consider the social context that shapes decision-making around drought risk management, such as cultural beliefs and traditional practices (Riessman, 2008). In addition, the data collected through both quantitative and qualitative methods was triangulated to ensure the robustness and validity of the findings by comparing data from diverse sources (surveys, interviews, FGDs) to identify convergence and divergence (Flick, 2018). This process will allow for a more comprehensive understanding of community-driven drought risk management strategies in the Bale zones.
3 Results and discussions
3.1 Demography and socio-economic status of study area community
The household survey, focus group discussion and key informant interview result suggests that pastoral and agro-pastoral activities remain the dominant economic drivers in the region while other livelihood strategies are on their early stage and introduced by developmental agents or organizations. In addition, the FGD and KII show that crop productions and all other income sources except livestock rearing is dominated by Youngers aged up to 35 years; while older are sticks to livestock only. The household surveys (n = 288) revealed gender imbalance, with a higher representation of male participants (80.5%) compared to females (19.9%). This imbalance is due to cultural and religious norms. In addition, at the time of data collection most of females migrated to other nearby areas and relatives taking their children while men remained at home to treat their livestock. Future research should employ strategies to ensure more balanced participation, such as conducting interviews at convenient times for women and offering childcare options.
Livelihood strategies varied, with pure pastoralists (41.8%), agro-pastoralists (40.5%), other livelihoods (11.7%), farm owners (7%), small businesses (6%) and other income sources (4.7%). Pure pastoralists group relies primarily on livestock, including cattle, goats, sheep, camels, and equines. The specific composition of herds might vary depending on cultural preferences, ecology, and market demands. Agro-pastoralists households combine livestock rearing with crop cultivation (maize, sorghum, teff, mung beans, and sesame). A small percentage reported income sources beyond pastoral and agro-pastoral activities and limited land ownership for large-scale farming. Small Businesses’ (6%) presence indicates some economic diversification.
The following Graph sheds light on the age, gender, and education levels of survey respondents in pastoral and agro-pastoral communities (Figure 2). A sizable portion of the surveyed population falls within the 18–35-year-old age range (16.1%). The younger population shows less experience coping with droughts compared to older generations. Regarding gender women make up 19.5% of the surveyed population and often play a critical role in managing household water and food security in these communities. In terms of education a substantial portion of the population (65.8%) has no formal education. This can significantly influence access to information and resources for coping with drought. Individuals with higher education (6.3%) reported better equipped to understand drought forecasts and implement mitigation strategies.
Figure 2. Demography status of study area community.
3.2 Distribution and frequency of drought perception
The research reveals a unanimous understanding across all communities (through surveys, FGDs, and key informant interviews) that rainfall patterns are negatively impacting livelihoods. Participants reported a decrease in rainfall, harming crop production and livestock rearing, the region’s main economic activities. Additionally, according to all FGD participants and key informants, a concerning trend of shorter rainy seasons alongside rising temperatures was observed. These findings align with existing research by Yimam and Mohammed (2016) who documented similar trends in southern Ethiopia. Furthermore, studies by Deressa et al. (2008), Bewket (2012), and Viste et al. (2012) support these observations, highlighting a broader national trend of decreasing rainfall and rising temperatures. This convergence of evidence underscores the significant challenge posed by changing climatic conditions.
The household surveys and qualitative data from key informant interviews and focus group discussions (FGDs) paint a concerning picture of increasing drought challenges in the study area. Both the frequency and spread of droughts throughout the primary and secondary rainy seasons (Genna and Hagaya) were reported as high. The years 2021 and 2022 saw extreme drought pressure across the region, with varying intensities impacting separate locations and survey results also supported these observations. A staggering 96.9% of participants reported an increase in drought frequency over the past 35 years, with over half (58.02%) experiencing annual droughts and another third (33%) feeling the impact every year. Community members, particularly elders participating in key informant interviews and FGDs, attributed this rise in drought frequency and intensity to several factors: deforestation, population growth, and overgrazing. They reminisce about a time when the area was covered by forests, and the two rainy seasons were sufficient to sustain both livestock and crops. This historical perspective sheds light on the potential causes of the current situation. Previously, communities could manage with some assistance if the expected heavy rains failed during one or both rainy seasons. However, recent droughts have become more severe and prolonged, making adaptation significantly harder. This increased variability in rainfall patterns disrupts traditional planning for the rainy season, hindering preparedness efforts. These observations align with existing research (Huho and Mugalavai, 2010; Kogan et al., 2016) highlighting the global rise in droughts. Additionally, studies by Deressa et al. (2010) and Bayissa et al. (2015) demonstrate a concerning trend of more frequent and intense droughts in Ethiopia over the past 3 decades.
3.3 General impacts of drought in the study area
Pastoralists in the study area painted a grim picture of the drought’s consequences. Key concerns included drying water sources, widespread crop failure, and livestock deaths due to lack of water and forage, and pasture degradation (Table 2). The economic impacts were equally severe, with rising food prices and plummeting livestock prices squeezing household budgets. Social issues arose as well, with children forced to drop out of school due to hardship. The rising temperatures further exacerbated the situation, contributing to poor human health and livestock infections. These impacts intensified during the recent drought period (2019–2022) and similar years preceding it. The burden of supporting the affected communities stretched beyond pastoral and agro-pastoral households. The government, NGOs, individuals, private sectors, and even the Ethiopian diaspora all felt the strain of helping in these drought-stricken areas. The study shows a grim scenario where drought has decimated livestock herds, a crucial source of income contributing to the country’s GDP. Crop failures further compound the issue, jeopardizing food security.
Table 2. Drought impact on pastoral and agro-pastoral communities in the bale zone.
Focus group discussions with community leaders and elders confirmed the widespread prevalence of the previously mentioned impacts. For instance, due to children dropping out of school and water scarcity, satellite schools were forced to close during the drought years of 2019–2022. This highlights the disruption to education caused by drought. Furthermore, the lack of water during prolonged dry seasons leads to frequent outbreaks of waterborne illnesses like diarrhea. Survey data provided a quantitative perspective on the severity of these impacts. All respondents (99.7% and 99.2% respectively) rated pasture deterioration and water scarcity as having a remarkably high impact during drought years. These factors significantly affect livestock health and survival, with 98.2% of respondents reporting extremely high livestock death rates due to drought. The economic consequences are equally concerning for 94.6% and 90.5% of respondents experiencing severe food scarcity and a decrease in household income.
The long dry season and drought years exacerbate these issues. According to key informant interview a huge portion of respondents (73.7%, 86.5%, and 97.5%) reported a high impact on health, household income, and food insecurity respectively during these extended dry periods. While less prevalent, other drought-related issues such as population migration (56.5%), unemployment (63.85%), conflict over resources (40.7%), and child school dropout (82.3%) were still considered to have a high impact by a substantial portion of the population. This data paints a clear picture of the devastating impact of drought on pastoral communities in the study area. It affects not only their livelihoods and wellbeing but also disrupts social structures and educational opportunities.
This situation aligns with a study by Bekele and Amsalu, 2012 exploring the impact of drought on Karrayyu pastoralists in the Fantale woredas. The study underscores the critical importance of understanding drought’s effects for all stakeholders involved in developing and implementing measures to mitigate its consequences (Pandey and Bhandari, 2009; Catley et al., 2021). By acknowledging the severity of the problem, relevant parties can work together to create effective solutions that protect these communities and their way of life. In addition, this finding aligns with existing research on the social and economic impacts of drought in various regions (Bekele, 2012; Lekapana, 2013; Kogan and Guo, 2016; Udmale et al., 2014; Menghistu et al., 2018), highlighting the widespread challenges faced by communities across the globe.
3.4 Impact of drought on women in Bale’s pastoral and agro pastoral communities
The below Table 3 shows the potential impact of drought on various aspects of women’s lives in Bale’s pastoral and agro pastoral communities. Drought significantly increases the workload for women, particularly in water collection (70%) and food management (60%). With more time spent fetching water (40%), other aspects of their lives can be strained. This strain is further compounded by reduced food availability (60%), potentially leading to higher malnutrition rates (40%) for both women and children. Utilizing drought-resistant crops (25%) and food preservation techniques (40%) were crucial coping mechanisms in these situations. Disruptions to traditional livelihoods (50%) force women to seek alternative income sources. Developing small businesses (30%) and joining income-generating groups (25%) are potential strategies. However, access to microloans or grants (20%) was limited, hindering their ability to establish these income sources. Limited water access (60%) increases the risk of waterborne illnesses (60%). Water treatment (50%) and prioritizing hygiene (70%) are essential coping mechanisms. However, only 40% have access to healthcare services, highlighting a potential gap in support systems. The increased workload limited women’s participation in household decision-making (20%), potentially reducing their influence on resource allocation during drought. Reduced access to nutritious food (40%) was leading to nutritional deficiencies and dietary diversification (35%) and rationing (60%) were potential coping mechanisms.
Table 3. Impact of drought on women in bale’s pastoral and agro pastoral communities.
The increased pressure on women (20%) due to these various burdens can indirectly impact girls’ education. Advocating for girls’ education (30%) and seeking support for childcare (20%) could help mitigate this impact. Encouraging girls’ participation in household tasks that are compatible with education (15%) might also be beneficial. Finally, the increased stress and anxiety (30%) due to various burdens highlight the need for social support from other women or family members.
The findings in this table align with existing research on the gendered impacts of drought in pastoral communities. For instance, studies by Scheelbeek et al., 2021; Awiti, 2022 highlight how drought disproportionately increases women’s workload, particularly in water collection and food management. This is further supported by Akpalu, D.A., 2005; Anbacha,and Kjosavik, 2019 who emphasizes the pressure on women to ensure household food security during times of drought. In addition, this aligns with Pukunyiem, 2020 who argues that women often play a crucial role in income generation during droughts, particularly through small-scale businesses and income-generating groups. Moreover, aligns with Moser (1998) who emphasizes how crises can exacerbate existing gender inequalities. Furthermore, this is supported by Moser and Felton (2010) who discuss how girls are often pulled out of school to help with household chores during crises.
3.5 Impact of drought on pastoral and agro-pastoral communities in study area
Pastoral communities represented respondents (100%) perceive reduced grazing land and water resources, leading to a high prevalence of livestock mortality (60%) and potential decreases in milk production (50%) and breeding cycles (50%). Most (80%) experience increased pressure on resources and overgrazing, with 40% facing social conflicts due to competition (Table 4). Significant income loss from livestock sales (70%) is another challenge. The coping mechanisms employed by pastoral communities focus on mobility (herding animals to distant pastures) for 50% of respondents, and collaborative grazing management for 30%. To manage livestock health, destocking weak animals (40%) and using drought-resistant fodder (25%) are utilized. Sharing resources and cooperation within communities are also important (20%). Like pastoral communities, most agro-pastoral communities (80%) perceive reduced grazing land and water resources. High percentages experience crop failure and reduced yields (90%), leading to increased reliance on livestock (reflected in the 60% who perceive difficult choices regarding selling livestock for food). Livestock mortality (50%) and decreased milk production (40%) are also concerns, though social conflicts are a potential concern for a smaller portion (20%) compared to pastoral communities. The majority (70%) report increased pressure on resources and overgrazing, with half (50%) perceiving increased vulnerability. Agro-pastoral communities utilize mobility for livestock less frequently (30%) due to potential limitations on suitable grazing areas. Collaborative grazing management (20%) and destocking (30%) are still practiced. Utilizing drought-resistant crops is a potential strategy (20%) under practice with a lower percentage of community members (model farmers). Diversifying income sources (40%) and seeking external support (food aid) (30%) are part of crucial strategies for these communities.
Table 4. Impact of drought on pastoral and agro-pastoral communities in study area.
The general output demonstrates strong parallels with existing research on how droughts differentially impact pastoral and agro-pastoral communities. For pastoral communities, the perceived near-universal reduction in grazing land and water resources (100%) aligns with studies by Tolera, and Senbeta, (2020) highlighting how droughts force pastoralists to travel further for sustenance. Similarly, the high prevalence of perceived livestock mortality (60%) echoes is in line with Anbacha, and Kjosavik, 2019 work on the devastating impact of drought on livestock wealth and food security. The potential for social conflicts due to competition (40%) resonates with Jury, and Vaux, (2007) emphasis on how crises can exacerbate existing tensions over scarce resources.
3.6 Pastoralists and agro-pastoral drough trisk Adaptation contingency planning and preparedness
3.6.1 Pastoralists’ perception and adaptation strategies for drought
Scientifically human activities like population growth, agricultural expansion, and deforestation contribute to droughts. In the same way in the study area drought is a recurring natural phenomenon attributed to factors like population growth, agricultural expansion, and deforestation for charcoal production indicating human activity contribution to drought. However, the perception of drought’s causes varies among the pastoral communities. A survey conducted with 288 households confirmed this diversity of perspectives with varying degrees. In addition, focus group discussions and key informant interviews revealed a range of opinions, with some participants attributing drought solely to natural factors. In line with this approximately 60% of discussants considered drought a natural disaster, while 31% of them believed human activities were the culprit. The remaining 9% saw a combination of both factors at play. This aligns with existing research by Hassen (2008), Lekapana (2013), Ashraf and Routry (2013), Udmale et al. (2014), Mengistu (2016), and Menghistu et al. (2018) that resonates with research by suggesting that individual experiences and environmental knowledge significantly shape how people perceive drought’s causes.
3.6.2 Pastoralists and agro-pastoralists drought risk indigenous early warning system
In study indigenous early warning systems play a crucial role in mitigating drought’s impact. According to focus group discussion and key informant interview the primary function of elders know of having knowledge of forecasting the weather is to alert communities to potential droughts, allowing them to prepare and minimize losses in livestock, crops, and food security (Figure 3). In addition, the study observed that pastoral households in the Bale zone rely on technical indicators and traditional methods for weather forecasting and drought prediction. These methods, often passed down through generations and honed through experience with climate variability, empower elders to anticipate droughts and guide the community in taking measures to reduce associated risks. This highlights the value of integrating traditional knowledge with modern scientific approaches for a more comprehensive drought preparedness strategy.
Figure 3. List of Indigenous Early warning system.
According to the survey, FGD and KII, pastoral communities in the study area demonstrate a remarkable reliance on traditional knowledge systems (90.5%) for weather forecasting and drought prediction. Modern media sources and government warnings play a minor role (10.5%) compared to these time-tested methods passed down through generations. This traditional approach incorporates a variety of observations, including animal behavior (changes in bird calls, cattle behavior, even insect activity), plant behavior (the timing and presence of leaves on specific trees as a signal for rain), and celestial observations (star and moon arrangements, wind direction) to predict rainfall patterns and potential droughts. By combining this traditional knowledge with modern scientific approaches, a more comprehensive drought preparedness strategy can be developed for the wellbeing of both communities and their livestock.
The study also explored the role of animal behavior in weather prediction. While some might dismiss this practice, locals believe animals can sense changes in their environment. For instance, they observe ant behavior, interpreting their relocation to secure areas as a sign of impending weather shifts. Similarly, frog calls and movements are used to forecast weather patterns. According to FGD and KII about 85% of weather forecasting and drought prediction is almost accurate, the implementation by local community is around 58.8% due to cultural view the community has for their livestock. These findings highlight the intricate ways in which pastoral communities have learned to interpret the natural world around them. The general finding of this study aligns with research by Wario (2011) in Borena and a 2012 study by Khetran, suggesting that animals might indeed detect storms and exhibit specific behaviors before they arrive.
3.7 Pastoralists and agro-pastoralists drought risk anticipatory action and coping mechanisms
The consolidated findings from surveys, focus group discussions (FGDs), and key informant interviews (KIIs) offer valuable insights into the community’s current comprehension of anticipatory action, their perception of existing risks, preparedness capacity, and willingness to collaborate on enhancing a proactive approach towards drought mitigation. Respondents observed that anticipatory action involves utilizing early warning systems to prompt pre-planned interventions aimed at protecting families and their assets prior to a disaster. Participants indicated a readiness to proactively respond to drought warnings by implementing pre-established measures such as distributing drought-resistant seeds, selling livestock before market prices drop, or securing access to alternative water sources.
This proactive strategy enhances community resilience by emphasizing two critical capabilities. Firstly, it involves the ability to anticipate risks through pre-emptive assessment of potential drought threats, enabling the development of appropriate mitigation strategies. Secondly, communities are encouraged to prepare and adjust by providing them with tools and resources to make informed decisions amidst uncertain future risks. Adopting anticipatory action enables communities to shift from a reactive to a proactive stance, facilitating the preservation of lives, protection of assets, and minimization of overall disaster impact, thereby fostering a more secure and resilient future.
Resource management emerges as a vital component of community survival, with most participants (90%) engaging in early livestock grazing practices to optimize resource use and animal wellbeing (Table 5). Similarly, adjusting planting schedules based on rainfall patterns is universal (92%). These practices highlight the community’s pragmatic and adaptable approach towards resource utilization. Furthermore, a substantial percentage (60%) rely on traditional methods such as constructing open ponds (62.8%) and strategic migration for water and forage (81.9%). The widespread adoption of communal enclosures (96.5%) reflects the community’s adaptability to evolving environmental and social challenges. Additionally, a sizable portion (over 60%) utilize livestock distribution across zones (61.7%) and alternative feed sources like evergreen tree leaves (75%) to supplement grazing resources. This find is inconsistent with research report of Duguma and Janssens, 2021 on assessment of livestock feed resources and coping strategies with dry season feed scarcity in mixed crop–livestock farming systems Agriculture is essential for ensuring food security, with over 80% of individuals cultivating drought-resistant crops such as sorghum and millet (Table 6). The majority also prioritize short-season, high-yielding varieties of these crops, with over 90% adjusting sowing times to optimize planting based on weather patterns. Additionally, 60% of communities adopt improved crop varieties and practice intercropping to further enhance yield and soil health.
Table 5. Livestock sector coping mechanisms for drought management.
Table 6. Agricultural practices for drought management in bale zones.
In addition to recovery programs, livelihood diversification plays a crucial role in providing a safety net during droughts (Table 7). A significant majority (over 60%) of community members engage in alternative income sources such as petty trade or transportation services (63.1%), displaying their entrepreneurial mindset. This is further supported by robust social safety nets within the communities, with many individuals adapting their livelihoods (83%) and seeking refuge with relatives in less affected areas (48.2%) during times of crisis. Another prevalent strategy is the distribution of family labor across various activities (54.6%), further reinforcing the community’s resilience is moderately prevalent (40%–60%).
Table 7. Livelihood diversification strategies for drought management and coping.
4 Discussion, conclusion and recommendations
4.1 Discussion
The household surveys, key informant interviews, and focus group discussions conducted in the study area have revealed a worsening drought situation, with high frequency and spread reported during both the primary and secondary rainy seasons in 2021 and 2022. The survey results indicate a significant 96.9% increase in drought frequency over the past 35 years, with more than half of the participants experiencing annual droughts. These findings are consistent with previous research by Huho and Mugalavai (2010) and Kogan et al. (2016) that highlight a global rise in droughts, as well as studies by Deressa et al. (2008) and Bayissa et al. (2017) showing more frequent and intense droughts in Ethiopia. The changing rainfall patterns have had a negative impact on livelihoods, with decreased overall rainfall harming crop production and livestock rearing (Bekele, 2015). Additionally, participants have noted shorter rainy seasons and rising temperatures, which align with research by Yimam and Mohammed (2016), Deressa et al. (2008), Bewket (2012), and Viste et al. (2013) indicating a national trend of decreasing rainfall and increasing temperatures.
Droughts in Bale zones of Ethiopia disproportionately burden women in pastoral and agro-pastoral communities. In support of this finding, the studies by Cruikshank, 2010, and Quandt (2019) show a significant increase in their workload, particularly for water collection and food management, straining their time and resources. Ngoc et al. (2023) further highlight that droughts heighten the risk of malnutrition and waterborne diseases for women and children due to biological vulnerabilities and caregiving roles. The study has also revealed a diversity of perspectives among pastoral communities regarding drought causation, with approximately 60% of participants viewing drought solely as a natural phenomenon, 31% attributing drought entirely to human activities, and the remaining 9% acknowledging the interplay of both natural and human-induced factors. Pastoral households in the Bale zone heavily rely on traditional methods for weather forecasting and drought prediction, with a reported reliance of 90.5% on traditional knowledge systems, Abate, 2016; McOmber, 2020 reported inconsistent concept in southern ethiopia and africa. The study also suggests an 85% accuracy rate in weather forecasting using traditional methods, although implementation by communities is around 58.8%. These findings underscore the importance of how pastoral communities interpret the natural world around them and align with research by Abarufa (2011), Svoboda et al., 2011 and Khetran et al. (2012) suggesting animals can detect storms and exhibit specific pre-emptive behaviors.
The study delves into the potential for a change in thinking in how Bale communities approach drought mitigation with the concept of anticipatory action, which leverages early warning systems to trigger pre-planned interventions before a disaster unfolds that in line with Anita et al., 2010; Abdela 2022 finding. The study suggests that communities are open to moving beyond a reactive stance of simply waiting for droughts to arrive, instead utilizing early warnings to activate pre-established actions like the concept reported by Desta, 2013. The finding that over 62.8% of respondents participate in preparing ponds in the study area aligns with Agrawal, and Saberwal, 2004 research on communal resource management in pastoral societies, showcasing the communal effort and cultural tradition of Bale communities. Additionally, the high prevalence of migration (81.9%) as the primary coping mechanism during hardships underscores the crucial role seasonal migration plays in ensuring the survival of pastoral communities during harsh climatic conditions, aligning with existing research by Hasan (2008), Bekele and Amsalu, 2012, Abdulatife and Ebro (2015), and Teshome (2016), as well as research by Ellis and Freeman (2004) and Leweri (2022). Moreover, the study highlights a shift away from traditional communal migration practices towards individual approaches like enclosure due to the decreasing availability of grazing land in the Bale lowlands, with 96.5% of respondents ranking individual migration as the most common strategy. This reflects the challenges faced by pastoral communities, with government directives potentially contributing to the shift. Additionally, splitting livestock into different areas and employing a zonal livestock distribution strategy can minimize overall herd losses during droughts, aligning with research by Kurukulasuriya and Rosenthal (2013), Hassan (2008), Abate, et al., 2009 and Huho et al. (2011) on the benefits of diversification in promoting the long-term sustainability of the rangeland ecosystem.
The research highlights the crucial role of herd diversification among pastoral communities in the Bale lowlands, enabling them to cope with harsh environmental conditions and adapt to a changing climate, as emphasized by researchers Ifejika (2010), Teshome (2016), and Rojas et al. (2017). To combat drought, Bale pastoral communities demonstrate remarkable innovation by cultivating drought-resistant crops, adopting intercropping techniques, and prioritizing female-dominated herds for long-term herd recovery. These strategies showcase their commitment to food security. This strategy, supported by research from Vandermeer (1992), Degefa, 2008 and Ayanlade et al. (2018), serves as a form of crop insurance and enhances productivity while mitigating risks associated with monoculture cropping systems. The study also reveals a shift towards agro-pastoralism among Bale pastoral communities, integrating crop cultivation into their practices to diversify livelihoods and address challenges such as population growth and environmental change, in line with research by Degefa, 2008,Lenaiyasa et al. (2020) and Alary et al. (2022).
4.2 Conclusion
The research in Bale zone southeast Ethiopia, reveals a unanimous understanding across communities: declining rainfall patterns are negatively impacting livelihoods. This decreases, alongside rising temperatures, aligns with existing national and global trends. Both surveys and qualitative data paint a concerning picture of intensifying droughts. Droughts are increasing in frequency and intensity, disrupting traditional agricultural practices. Community elders attribute this shift to deforestation and overgrazing, highlighting potential causes demanding further investigation.
Water source depletion, widespread crop failures, and livestock deaths due to lack of water and forage have crippled livelihoods. Social issues like school dropouts and health problems exacerbate the situation. Drought decimates livestock herds, a crucial economic pillar, and jeopardizes food security through crop failures. Survey data quantifies the severity, with near-unanimous reports of extremely high impacts on pasture, water scarcity, and livestock death rates. The economic consequences concern a vast majority experiencing severe food scarcity and income decline. While less prevalent, issues like population migration, unemployment, conflict, and school dropout still hold a high impact for a substantial portion of the population. Focus groups with leaders reveal animal mortality, food scarcity, and water scarcity as top concerns, highlighting the profound impact on the foundation of pastoral life. The situation worsens during prolonged dry seasons, with some resorting to migration that can lead to conflict.
Drought disproportionately burdens Bale’s pastoral women. Workloads surge in water collection and food management. Malnutrition risk rises for women and children due to reduced food availability. Women seek alternative income, but limited access to microloans hinders efforts. Water scarcity increases waterborne illness risk, highlighting the need for improved water treatment and sanitation. Increased workload also reduces women’s decision-making power and access to nutritious food.
The study reveals significant impacts of drought on both pastoral and agro-pastoral communities in Bale. Reduced grazing land and water scarcity cripple livelihoods, leading to high livestock mortality and declining milk production. Pastoral communities face intense pressure and potential conflict due to overgrazing. Both groups experience income loss, but agro-pastoralists are additionally burdened by crop failure, forcing difficult choices. Mobility, destocking, collaborative grazing, and resource sharing are crucial coping mechanisms, with agro-pastoralists also utilizing drought-resistant crops and income diversification.
Human contributions like population growth and deforestation contribute to droughts in Bale. However, community perceptions vary, with some attributing drought solely to natural factors while others acknowledge human influence. Bale’s pastoralists rely heavily (90.5%) on traditional methods for weather forecasting (animal behavior, plants, stars,etc.) passed down through generations. Modern methods play a minor role. This study highlights the value of combining traditional knowledge with science for better drought preparedness.
The study highlights a shift towards proactive drought mitigation in Bale communities. They value early warnings and envision using them to take pre-emptive actions like distributing drought-resistant seeds or securing water sources. This proactive approach focuses on understanding potential threats and being prepared to adapt. Bale’s pastoralists display remarkable resilience against droughts through a multifaceted approach. They leverage seasonal migration and strategic herd management to secure water, pasture, and animal health. This includes diversifying herds with drought-resistant species and strategically selling livestock before droughts. Furthermore, over 97% cultivate drought-resistant crops, employing intercropping techniques to maximize resources. These findings highlight the pastoral communities’ deep understanding of their environment, resourcefulness, and long-term planning for the wellbeing of their herds and communities.
4.3 Recommendations
The study’s findings paint a clear picture of the challenges faced by Bale’s pastoral communities–a relentless cycle of drought exacerbated by water scarcity. Based on these insights, the following recommendations are proposed to enhance community resilience and promote long-term sustainability.
4.3.1 Prioritizing water security
Governmental and non-governmental organizations (NGOs) at all levels should prioritize the construction of permanent open ponds, maintenance of existing ones, and exploration of groundwater drilling or alternative water sources. Introducing irrigation schemes, where feasible, can further bolster water security and promote drought-resistant agriculture.
4.3.2 Sustainable resource management
Implementing effective rangeland management practices is crucial for long-term sustainability. Collaborative efforts are needed to develop and enforce regulations to prevent overgrazing and promote responsible resource utilization. Conservation initiatives focusing on soil and water preservation should be prioritized to ensure the health of the ecosystem upon which these communities depend.
4.3.3 Early warning systems
The valuable traditional weather forecasting methods employed by pastoral communities should be strengthened by integrating them with modern technologies for more accurate and advanced drought prediction. The government should establish reliable channels for disseminating real-time, drought-predicting information using contemporary technologies to allow communities to prepare effectively.
4.3.4 Strengthening livelihoods and food security
Research institutions and agricultural extension programs should focus on introducing and promoting drought-resistant crop varieties suitable for the Bale region. Encouraging the cultivation of short-season crops can provide a vital source of food during drought periods.
4.3.5 Community capacity building
Investing in comprehensive awareness programs at all levels is essential to maximize the effectiveness of existing drought coping and adaptation strategies within communities. Governmental and non-governmental actors should prioritize long-term interventions that empower communities to become self-reliant rather than relying solely on short-term, consumptive aid.
4.3.6 Market facilitation and risk management
During droughts, the government and other stakeholders should facilitate and support the livestock market by improving infrastructure and market access for pastoralists. Community-based drought risk contingency planning and preparedness efforts should be developed, aligning with the government’s existing plans to ensure a comprehensive and coordinated approach. By implementing these recommendations, policymakers, NGOs, research institutions, and the pastoral communities themselves can work collaboratively to build a more secure and sustainable future for Bale. By combining traditional knowledge with scientific advancements and prioritizing long-term solutions, this region can weather the storms of drought and ensure the continued flourishing of its unique pastoral culture.
Data availability statement
The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.
Ethics statement
Ethical review and approval was not required for the study on human participants in accordance with the local legislation and institutional requirements. Written informed consent from the (patients/participants OR patients/participants legal guardian/next of kin) was not required to participate in this study in accordance with the national legislation and the institutional requirements.
Author contributions
UG: Conceptualization, Data curation, Formal Analysis, Funding acquisition, Investigation, Methodology, Project administration, Resources, Software, Supervision, Validation, Visualization, Writing–original draft, Writing–review and editing.
Funding
The author(s) declare that no financial support was received for the research, authorship, and/or publication of this article.
Acknowledgments
The author would like to extend special gratitude to the Dar Al Fiker Foundation Ethiopia for their generous funding of this research. The foundation’s financial support has enabled me to dedicate more time and resources to this research and their motivational activities have inspired me to share my experiences and contribute to the community in meaningful ways.
Conflict of interest
The author declares that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
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References
Abate, T. (2016). Contribution of indigenous knowledge to climate change and adaptation response in Southern Ethiopia. J. Earth Sci. Clim. Chang. 7, 377. doi:10.4172/2157-7617.1000377
Abate, T., Ebro, A., and Nigatu, L. (2009). Pastoralists perceptions and rangeland evaluation for livestock production in Southeastern Ethiopia. Livest. Res. Rural Dev. 21 (7), 1–13.
Abdela, U. (2022). Climate change adaptation and mitigation strategies in madda walabu district, bale zone, southeast Ethiopia. Int. J. Ecol. 2022, 1–12. doi:10.1155/2022/5658440
Abdulatife, M., and Ebro, A. (2015). Assessment of pastoral perceptions towards range and livestock management practices in Chifra district of Afar regional state, Ethiopia. For. Res. 4 (144), 2. doi:10.4172/2168-9776.1000144
Abubakar, I. U., and Yamusa, M. A. (2013). Recurrence of drought in Nigeria: causes, effects, and mitigation. Int. J. Agric. Food Sci. Technol. 4 (3), 169–180.
Adjorlolo, L. K., Timpong-Jones, E. C., Boadu, S., and Adogla-Bessa, T. (2016). Potential contribution of neem (Azadirachta indica) leaves to dry season feeding of ruminants in West Africa. Livest. Res. Rural Dev. 28 (5), 75.
Agrawal, A., and Saberwal, V. K. (2004). Whither south Asian pastoralism? An introduction. Nomadic Peoples 8 (2), 36–53.
Akpalu, D. A. (2005). Response scenarios of households to drought-driven food shortage in a semi-arid area in South Africa. Johannesburg (South Africa): Doctoral dissertation, University of the Witwatersrand.
Alary, V., Caulfield, M. E., Amsidder, L., Juanes, X., Boujenane, I., Sraïri, T. M., et al. (2022). Heterogeneity of resilience of livelihood strategies in pastoral and agropastoral farming systems of rural semi-arid to arid areas in Morocco. Front. Sustain. Food Syst. 5, 723994. doi:10.3389/fsufs.2021.723994
Alemayehu Tegegn, D. (2023). The trigger of Ethiopian famine and its impacts from 1950 to 1991. Cogent Arts Humanit. 10 (1), 2264017. doi:10.1080/23311983.2023.2264017
Amsale, K. T. (2010) “The impact of environmental and political influences on pastoral conflict inSouthern Ethiopia,” In conference on climate change in Trongheim.
Anbacha, A. E., and Kjosavik, D. J. (2019). The dynamics of gender relations under recurrent drought conditions: a study of Borana Pastoralists in Southern Ethiopia. Hum. Ecol. 47, 435–447. doi:10.1007/s10745-019-00082-y
Anita, W., Dominic, M., and Neil, A. (2010). Climate change and agriculture impacts, adaptation, and Mitigation: impacts, adaptation, and Mitigation. Paris, France: OECD publishing.
Asheber, S. A. (2010). Mitigating drought: Policy impact evaluation: a case of Tigray region, Ethiopia master's thesis. Enschede (Netherlands): University of Twente.
Ashraf, M., and Routray, J. K. (2013). Perception and understanding of drought and coping strategies of farming households in north-west Balochistan. Int. J. Disaster Risk Reduct. 5, 49–60. doi:10.1016/j.ijdrr.2013.05.002
Awiti, A. O. (2022). Climate change and gender in Africa: a review of impact and gender-responsive solutions. Front. Clim. 4. doi:10.3389/fclim.2022.895950
Ayanlade, A., Radeny, M., Morton, J. F., and Muchaba, T. (2018). Rainfall variability and drought characteristics in two agro-climatic zones: an assessment of climate change challenges in Africa. Sci. Total Environ. 630, 728–737. doi:10.1016/j.scitotenv.2018.02.196
Bale Zone Pastoral Area Development Office (BZPADO) (2022). Zonal drought assessment Report,BaleOromia region robe, Ethiopia.
Bayissa, Y., Tadesse, T., Demisse, G., and Shiferaw, A. (2017). Evaluation of satellite-based rainfall estimates and application to monitor meteorological drought for the Upper Blue Nile Basin, Ethiopia. Remote Sens. 9 (7), 669. doi:10.3390/rs9070669
Bekele, A., and Amsalu, A. (2012). Effects of drought on pastoral household in Fentale Woreda of Oromia regional state, Ethiopia. J. Environ. Issues Agric. Dev. Ctries. 4, 5–19.
Bekele, F. (2015). Characterizing current and future rainfall variability and its effect on wheat and barley production in Sinana District, Southeastern Ethiopia. Unpublished MSc Thesis: Haramaya University.
Belay, K., Beyene, F., and Manig, W. (2005). Coping with drought among pastoral and agro-pastoral communities in eastern Ethiopia. J. Rural Development/Nongchon-Gyeongje 28 (4), 185–210. doi:10.22004/ag.econ.288376
Bessachi, H., and Announ, F. (2023). “Food insecurity in the world in sustainable agricultural development,” in International journal of economic performance.
Bewket, W. (2012). Climate change perceptions and adaptive responses of smallholder farmers in central highlands of Ethiopia. Int. J. Environ. Stud. 69 (3), 507–523. doi:10.1080/00207233.2012.683328
Bishop, K., and Dimoulias, K. (2024). “Global challenges and trends affecting all children and young people and their environmental experiences,” in The routledge handbook on the influence of built environments on diverse childhoods, 9–22.
Blauhut, V. (2020). The triple complexity of drought risk analysis and its visualisation via mapping: a review across scales and sectors. Earth-Science Rev. 210, 103345. doi:10.1016/j.earscirev.2020.103345
Bogale, G. A., and Erena, Z. B. (2022). Drought vulnerability and impacts of climate change on livestock production and productivity in different agro-Ecological zones of Ethiopia. J. Appl. Animal Res. 50 (1), 471–489. doi:10.1080/09712119.2022.2103563
Bryan, E., Ringler, C., Okoba, B., Roncoli, C., Silvestri, S., and Herrero, M. (2013). Adapting agriculture to climate change in Kenya: household strategies and determinants. J. Environ. Manag. 114, 26–35. doi:10.1016/j.jenvman.2012.10.036
Catley, A., Stites, E., Ayele, M., and Arasio, R. L. (2021). Introducing pathways to resilience in the karamoja cluster. Pastoralism 11 (1), 28. doi:10.1186/s13570-021-00214-4
Cruikshank, A. (2010). These are our water pipes: sand dams, women and donkeys-dealing with water scarcity in arid lands.
de Brito, M. M. (2021). Compound and cascading drought impacts do not happen by chance: a proposal to quantify their relationships. Sci. Total Environ. 778, 146236. doi:10.1016/j.scitotenv.2021.146236
de Brito, M. M., Sodoge, J., Fekete, A., Hagenlocher, M., Koks, E., Kuhlicke, C., et al. (2024). Uncovering the dynamics of multi-sector impacts of hydrological extremes: a methods overview. Earth's Future 12 (1), e2023EF003906. doi:10.1029/2023EF003906
Degefa Tolossa, D. T. (2008). Livelihood transformation from pastoralism to agro-pastoralism as an adaptation strategy among the Urrane of north-eastern Ethiopia.
Delbiso, T. D., Altare, C., Rodriguez-Llanes, J. M., Doocy, S., and Guha-Sapir, D. (2018). Short and long-term droughts, food security and child mortality in Ethiopia: can sub-national surveys tell us more about the success of mitigation efforts? Field Exch. 57, 70.
Deressa, T., Hassan, R. M., and Ringler, C. (2008). Measuring Ethiopian farmers' vulnerability to climate change across regional states. Intl Food Policy Res. Inst.
Desta, S. (2013). “Transitions in pastoral practices and livelihoods under changing climate: the case of Borana pastoralists in Southern Ethiopia,” in Climate change vulnerability and risk assessment of agriculture and food security in Ethiopia, 141.
Duguma, B., and Janssens, G. P. (2021). Assessment of livestock feed resources and coping strategies with dry season feed scarcity in mixed crop–livestock farming systems around the gilgel gibe catchment, Southwest Ethiopia. Sustainability 13 (19), 10713. doi:10.3390/su131910713
Ellis, F., and Freeman, H. A. (2004). Rural livelihoods and poverty reduction policies. London, United Kingdom: Routledge.
Foran, M. P., Greenough, P. G., Thow, A., Gilman, D., Schütz, A., Chandran, R., et al. (2012). Identification of current priorities for research in humanitarian action: proceedings of the First Annual UN OCHA Policy and Research Conference. Prehospital disaster Med. 27 (3), 260–266. doi:10.1017/S1049023X12000672
Gashaw, T., Asresie, A., and Haylom, M. (2014). Climate change and livestock production in Ethiopia. Adv. Life Sci. Technol. 22, 39–42.
Gebrehiwot, T., Van der Veen, A., and Maathuis, B. (2011). Spatial and temporal assessment of drought in the Northern highlands of Ethiopia. Int. J. Appl. Earth Observation Geoinformation 13 (3), 309–321. doi:10.1016/j.jag.2010.12.002
Gebremeskel, E. N., Desta, S., and Kassa, G. K. (2019). “Pastoral development in Ethiopia,” in Trends and the way forward. Development knowledge and learning (Washington, DC: World Bank and the International Fund for Agricultural Development).
Habte, M., Eshetu, M., Maryo, M., Andualem, D., and Legesse, A. (2022). Effects of climate variability on livestock productivity and pastoralists perception: the case of drought resilience in Southeastern Ethiopia. Veterinary Animal Sci. 16, 100240. doi:10.1016/j.vas.2022.100240
Hansen, J. W., Dilley, M., Goddard, L. M., Conrad, E., and Erickson, P. (2004). Climate variability and the millennium development goal hunger target.
Hassen, A. (2008). Vulnerability to drought risk and famine: Local responses and external interventions among the Afar of Ethiopia, a study on the Aghini Pastoral Community (Doctoral dissertation).
Hidosa, D., and Guyo, M. (2017). Climate change effects on livestock feed resources: a review. J. Fish. Livest. Prod. 5, 259. doi:10.4172/2332-2608.1000259
Huho, J. M., and Mugalavai, E. M. (2010). The effects of droughts on food security in Kenya. Int. J. Clim. Change Impacts Responses 2 (2), 61. doi:10.18848/1835-7156/CGP/v02i02/37312
Huho, J. M., Ngaira, J. K., and Ogindo, H. O. (2011). Living with drought: the case of the Maasai pastoralists of northern Kenya. Educ. Res. 2 (1), 779–789.
Ifejika Speranza, C. (2010). Drought coping and adaptation strategies: understanding adaptations to climate change in agro-pastoral livestock production in Makueni district, Kenya. Eur. J. Dev. Res. 22, 623–642. doi:10.1057/ejdr.2010.39
IPCC (2012). Managing the risks of extreme events and disasters to advance climate changeadaptation. A special Rep. Work. groups I II Intergov. Panel 69 Clim. Change.
IPCC (2014). Climate change 2014; impacts, adaptations, and vulnerability: regional 694 Aspects,Working group II contribution to the fifth assessment report of intergovernmental panel on climate change. Cambridge: Cambridge University Press.
Jury, W. A., and Vaux Jr, H. J. (2007). The emerging global water crisis: managing scarcity and conflict between water users. Adv. Agron. 95, 1–76. doi:10.1016/S0065-2113(07)95001-4
Kamara, A. B. (2003). Role of policies and development interventions in pastoral resource management: the Borana rangelands in southern Ethiopia. Nairobi, Kenya: ILRI aka ILCA and ILRAD.
Khetran, R. B., Khan, S., and Chaudhry, W. (2012). 02 indigenous knowledge, early warning system and disaster management: a case study of khetran community in balochistan, Pakistan. J. Gend. Soc. Issues 11 (1).
Kogan, F., and Guo, W. (2016). Early twenty-first-century droughts during the warmest climate. Geomatics, Nat. hazards risk 7 (1), 127–137. doi:10.1080/19475705.2013.878399
Kogan, F., Guo, W., Strashnaia, A., Kleshenko, A., Chub, O., and Virchenko, O. (2016). Modelling and prediction of crop losses from NOAA polar-orbiting operational satellites. Geomatics, Nat. Hazards, Risk 7 (3), 886–900. doi:10.1080/19475705.2015.1009178
Kurukulasuriya, P., and Rosenthal, S. (2013). Climate change and agriculture: a review of impacts and adaptations.
Lekapana, P. L. (2013). Socioeconomic impacts of drought on pastoralists, their coping strategies, and government interventions in Marsabit County, Kenya. San Francisco (CA): Doctoral dissertation, University of Nairobi.
Lemma, A. (2013). “Assessment of adaptation mechanisms of agro-pastoralists to climate change in oromia region,” in Ethiopia: the case of kofele and kore districts (London, United Kingdom: Doctoral dissertation, St. Mary's University).
Lenaiyasa, M. L., Bruyere, B. L., Salerno, J., and Pickering, T. (2020). Pastoralists’ use of income diversification as a strategy for adapting to social-ecological change in Samburu, Kenya. Reg. Environ. Change 20, 1–11. doi:10.1007/s10113-020-01612
Leweri, C. (2022). Herding strategies under shifting rainfall conditions: implications for rangeland conservation and pastoralist livelihoods (Doctoral dissertation, NM-AIST).
Manger, L. (2000). East African pastoralism and underdevelopment: an introduction. Pastor. Environ. Exp. Gt. horn Afr. Addis Ababa OSSREA, 1–18.
Masih, I., Maskey, S., Mussá, F. E. F., and Trambauer, P. (2014). A review of droughts on the African continent: a geospatial and long-term perspective. Hydrology earth Syst. Sci. 18 (9), 3635–3649. doi:10.5194/hess-18-3635-2014
Melaku, E. (2013). Assessment of drought early warning in Ethiopia: a Comparison of WRSI by surface energy balance and soil water balance. Netherlands, Enschede: University of Twente. MSC Thesis.
Menghistu, H. T., Mersha, T. T., and Abraha, A. Z. (2018). Farmers’ perception of drought and its socioeconomic impact: the case of Tigray and Afar regions of Ethiopia. J. Appl. Animal Res. 46 (1), 1023–1031. doi:10.1080/09712119.2018.1450752
Mengistu, D. (2016). Impacts of drought and conventional coping strategies of Borana community, southern Ethiopia. Res. Humanit. Soc. Sci. 6 (23), 29–37.
Mertz, O., Mbow, C., Reenberg, A., and Diouf, A. (2009). Farmers’ perceptions of climate change and agricultural adaptation strategies in rural Sahel. Environ. Manag. 43, 804–816. doi:10.1007/s00267-008-9197-0
Mishra, A. K., and Singh, V. P. (2010). A review of drought concepts. J. hydrology 391 (1-2), 202–216. doi:10.1016/j.jhydrol.2010.07.012
Mogotsi, K., Nyangito, M. M., and Nyariki, D. M. (2013). The role of drought among agro-pastoral communities in a semi-arid environment: the case of Botswana. J. arid Environ. 91, 38–44. doi:10.1016/j.jaridenv.2012.11.006
Mohammed, Y., Yimer, F., Tadesse, M., and Tesfaye, K. (2017). Meteorological drought assessment in north east highlands of Ethiopia. Int. J. Clim. Change Strategies Manag. 10 (1), 142–160. doi:10.1108/IJCCSM-12-2016-0179
Moser, C., and Felton, A. (2010). The gendered nature of asset accumulation in urban contexts: Longitudinal results from Guayaquil, Ecuador (No. 2010/17). WIDER Work. Pap.
Ngoc, T. T. H., Pramanik, S. A., and Khanh, P. T. (2023). The relationship between gender and climate change in vietnam. The seybold report.
Oba, G. (1998). Effects of excluding goat herbivory on Acacia tortilis woodland around pastoralist settlements in northwest Kenya. Acta Oecol. 19 (4), 395–404. doi:10.1016/S1146-609X(98)80044-1
Pukunyiem, M. O. (2020). Gender vulnerability to drought in the upper east region of Ghana: a comparative study of bongo and talensi districts (Doctoral dissertation).
Quandt, A. (2019). Variability in perceptions of household livelihood resilience and drought at the intersection of gender and ethnicity. Clim. Change 152 (1), 1–15. doi:10.1007/s10584-018-2343-7
Scheelbeek, P. F., Dangour, A. D., Jarmul, S., Turner, G., Sietsma, A. J., Minx, J. C., et al. (2021). The effects on public health of climate change adaptation responses: a systematic review of evidence from low-and middle-income countries. Environ. Res. Lett. 16 (7), 073001. doi:10.1088/1748-9326/ac092c
Scoones, I. (2004). Climate change and the challenge of non-equilibrium thinking. IDS Bull. 35 (3), 114–119.
Sharma, J., and Ravindranath, N. H. (2019). Applying IPCC 2014 framework for hazard-specific vulnerability assessment under climate change. Environ. Res. Commun. 1 (5), 051004. doi:10.1088/2515-7620/ab24ed
Sinay, L., and Carter, R. W. (2020). Climate change adaptation options for coastal communities and local governments. Climate 8 (1), 7. doi:10.3390/cli8010007
Svoboda, M. D., Smith, K., Widhalm, M., Woudenberg, D. L., Knutson, C. L., Sittler, M., et al. (2011). Drought-ready communities: a guide to community drought preparedness.
Tache, B. (2008). Pastoralism under stress: resources, institutions, and poverty among the Borana Oromo in southern Ethiopia. Ås, Norway: Norwegian University of Life Sciences, Department of International Environment and Development Studies, xi+–47.
Temesgen, A. K. (2010). Climate change to conflict. Lessons South. Ethiop. North. Kenya. Fafo Rep. 9.
Teshome, A. (2016). Indigenous ecological knowledge and pastoralist perception on rangeland management and degradation in Guji zone of south Ethiopia. Consilience (15), 192–218.
Tolera, T., and Senbeta, F. (2020). Pastoral system in the face of climate variability: household adaptation strategies in Borana Rangelands, Southern Ethiopia. Environ. Dev. Sustain. 22, 3133–3157. doi:10.1007/s10668-019-00339-y
Udmale, P., Ichikawa, Y., Manandhar, S., Ishidaira, H., and Kiem, A. S. (2014). Farmers׳ perception of drought impacts, local adaptation and administrative mitigation measures in Maharashtra State, India. Int. J. disaster risk Reduct. 10, 250–269. doi:10.1016/j.ijdrr.2014.09.011
Viste, E., Korecha, D., and Sorteberg, A. (2013). Recent drought and precipitation tendencies in Ethiopia. Theor. Appl. Climatol. 112, 535–551. doi:10.1007/s00704-012-0746-3
Wang, J., He, Z., and Weng, W. (2020). A review of the research into the relations between hazards in multi-hazard risk analysis. Nat. Hazards 104 (3), 2003–2026. doi:10.1007/s11069-020-04259-3
Wario, A. J. (2011). Climate change and variability and its impact on the Livelihood of pastoralists: case study in dire Woreda of Borana zone, Oromia region. Addis Ababa, Ethiopia: Doctoral dissertation, Addis Ababa University.
Weldegebriel, Z. B., and Prowse, M. (2013). Climate-change adaptation in Ethiopia: to what extent does social protection influence livelihood diversification? Dev. Policy Rev. 31, o35–o56. doi:10.1111/dpr.12038
Yemane, M. (1967). Elemantary sampling theory. Englewood Cliffs, New Jersey, USA: Printice-Hall Inc, 11009297.
Keywords: adaptation strategies, bale pastoral, contingency plan, drought, preparedness
Citation: Abdela U (2024) Assessment of community-driven drought risk management strategies in pastoral and agro-pastoral district of Bale zones south east Ethiopia. Front. Environ. Sci. 12:1411138. doi: 10.3389/fenvs.2024.1411138
Received: 02 April 2024; Accepted: 11 June 2024;
Published: 18 July 2024.
Edited by:
Giulio Castelli, University of Florence, ItalyReviewed by:
Lorenzo Villani, Università di Firenze, ItalyLouise Cavalcante, Wageningen University and Research, Netherlands
Copyright © 2024 Abdela. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Umer Abdela, dW1lcmFiZGVsYTIwMTRAZ21haWwuY29t
†ORCID ID:Umer Abdela, orcid.org/0000-0003-1280-7162