Livelihood resilience in the face of recurring floods: an empirical evidence from Northwest Ethiopia

Abstract

Background

The recent trend of increasing incidents of floods in Ethiopia is disrupting the livelihoods of a significant proportion of the country’s population. This study assesses the factors that shape the resilience and the vulnerability of rural households in the face of recurring floods by taking the case of Dembia district of Northwest Ethiopia as one of the flood-prone areas in the country.

Results

The data for the study were collected through a survey of 284 households, two focus group discussions, and 12 key informant interviews. Principal Component Analysis and simple linear regression were used for the analysis. The former served both for data reduction and identification of the dominant factors that explain resilience to recurring flood hazards while the latter was used to check the relationship between resilience and vulnerability. Findings indicate that access and use of livelihood resources such as size of farmlands, availability of farm oxen, credit as well as ability to draw help from social networks were found to be the most important factors that determine the resilience of households to floods. Similarly, the coping strategies employed by households were found to be constrained mainly by the scale and impact of the recent floods and lack or shortage of basic infrastructural and social facilities.

Conclusions

The results confirmed that most of the traditional coping strategies employed by households failed to effectively help households offset the impacts of flooding. Given the livelihood context of smallholder farming system in the studied area, context specific institutional interventions such as the integrated use of both safety nets and cargo nets may help communities to overcome livelihood predicaments associated with the recurrent flood disasters. This implies that policy should focus more on addressing the factors that expose people to flood disasters and shape their resilience, rather than focusing on short-term emergency responses which seems to be the norm in much of the flood affected areas in the country.

Background

It is widely recognized that environmental hazards frequently affect the livelihoods of many people around the world. The effects of these hazards cannot be expected to be similar as people and nations differ in terms of their level of development, which largely determines their response to specific disasters.

Flooding is one of the most frequent and destructive environmental hazards that occur annually worldwide (United Nations International strategy for Disaster Reduction [UNISDR] (2015). The frequency and severity of flooding are also increasing in many parts of the world associated with population pressure, urbanization and climate change (Hirabayashi et al., 2013; Jongman et al., 2014). This is evident when one considers the number of people affected by flooding in recent decades. For instance, flooding accounts much of the loss event worldwide between 1980–2014 more than any other single disaster (Munich RE, 2015) and tops the list of natural disasters by economic damages in 2014 (Guha-Sapir et al., 2015). Flooding is also the leading disaster agent in the world in terms total number of reported disasters from 1900–2014 (see Additional file 1: Figure A) while it is the second largest natural hazard, next to drought, in terms of total number of affected persons between 1960 and 2015 (see Additional file 1: Figure B).

In Ethiopia, despite being given relatively less attention as compared to drought, flooding has long been recognized as one of the major environmental hazards that often develop into a disaster affecting the lives and livelihoods of people for many years. In fact, flooding and its damages are considered as a perennial phenomenon in the highlands (Disaster Prevention and Preparedness Commission [DPPC], 1994). The country’s proneness to non-drought disasters such as floods has been limited in the past in terms of frequency and scope (DPPC, 1997a).

However, the historical records on flood data suggests that Ethiopia faced 47 major floods since 1900, which affected close to 2.2 million people (You and Ringer, 2010). In this regard, many of the flood disasters occurred since 1980 (World Bank, 2010) (see also Table 1). This coupled with climate change and variability is likely to increase flooding as one of the major extreme events in the future posing a growing threat to many livelihoods (Intergovernmental Panel on Climate Change (IPCC), 2014; Savage et al., 2015). Flooding as a recurrent environmental hazard is particularly felt in areas where people are already vulnerable to any adverse climatic event as a result of weakened resilience. For instance, an estimated 210,600 people were affected by flooding only within three months (November, 2015–January, 2016) (United Nations Office for the Coordination of Humanitarian Affairs [UN-OCHA], 2016 p.1)

Table 1 Total damage due to natural disasters between 1900 and 2013 in Ethiopia

A complete national and regional disaggregated data on flood disasters is limited in Ethiopia (see Table 2). However, the available literature indicates that some areas in the country are far more frequently affected than others, to the extent of being labeled as ‘flood-prone areas’ (World Meteorological Organization (WMO), 2003; Nederveen et al., 2011; UN-OCHA, 2016). These areas include central and western zones of Tigray; North Gondar, North and South Wello, and Oromia zones of Amhara region which are often affected by flash flooding as well as those that are affected by riverine floods, which include almost all the major river basins and the Tana Basin (DPPC 1994; 1997b; Nederveen et al., 2011; UN-OCHA, 2016).

Table 2 Flood Disaster Statistics in Ethiopia between 1960 and 2013

The Amhara region as indicated above is one of the flood-prone areas in the country where severe and frequent floods affect a considerable number of people in recent years. In this regard, the limited available data on the effects of floods in the region indicate that riverine floods were recorded in 1966, 1967, 1974, and 1975. Severe flash floods have also been recorded in 1993 and 1996, with 72,569 people being affected. And a severe flooding in 2006, has affected 107,286 people, displacing 37,982, damaging crops on 18,000 ha of land in six zones (Disaster Prevention and Preparedness Agency [DPPA], 2007; Nederveen et al., 2011; UN-OCHA 2016). Moreover, seven districts in the region, which are all found around Lake Tana, are particularly well known for being frequently affected by both flash and riverine floods. One of these areas is Dembia district in North Gondar zone, which is highly affected by Megech, Derema and Gumero rivers that frequently overflow their banks affecting the nearby settled plains (DPPA, 2007) (see Additional file 1: Table A).

Flooding in Dembia district, has become all too common in recent years, and remains the most serious challenge to peoples’ livelihood with its short and long-term effects. As a result, some people were forced into destitution (UN-OCHA, 2006; DPPA, 2007; You and Ringer, 2010; Kreft et al., 2016; UN-OCHA, 2016). When this, coupled with the increasing flooding scenario predicted by the reports of the IPPC (2007; 2012; 2014) amplify the magnitude of the problem. Furthermore, the problem of flooding would particularly be worse for countries like Ethiopia with the majority of its population subjected to poverty and vulnerability to climatic shocks (Berhanu and Fekadu, 2015; Ethiopian Panel on Climate Change [EPCC], 2015; Savage et al., 2015). This in turn, justifies the need to study flooding as a livelihood problem since it creates downward pressures on livelihoods. The understanding of flooding as a livelihood shock also needs an analysis of resilience of livelihood systems in the face of the recurring flood disasters.

The concept of resilience has recently been widely promoted in many fields such as engineering, psychology, and ecology, very recently resilience has become widely used by humanitarian and development actors working across diverse thematic areas including, disaster risk reduction, climate change, ecosystem management, and food and nutrition security (Frankenberger et al., 2012; Constas and Barrett, 2013; Maxwell et al., 2013; Hoddinott, 2014; Razafindrabe et al., 2015). Building resilience of households, communities, and systems has also been considered as a crucial policy objective among various development frameworks including, the Sendai Framework for Disaster Risk Reduction (United Nations [UN], 2015a), the Paris Agreement on Framework Convention on Climate Change (UN, 2015b), and the Sustainable Development Goals (UN, 2015c). Resilience harbors different meanings in different contexts. In disaster risk reduction, it is broadly viewed as a concept that deals with a system’s capacity to anticipate, to cope, to absorb, adapt to, and recover from the adverse impact of hazards and reduce vulnerability (Razafindrabe et al., 2015; Tanner et al., 2015). The concept of vulnerability is often contrasted with resilience; however, it is an interlinked function of exposure, sensitivity, and adaptive capacity (Adger, 2006; IPCC, 2014). Being a common indicator, adaptive capacity, can be taken as a desirable characteristic of a system that minimizes vulnerability while enhances resilience at all levels (Engle, 2011; Frankenberger and Nelson, 2013). Following Maru et al. (2014), this study argues that there is a need to combine the two concepts since both are concerned with features that affect people’s ability to cope with and respond to change.

In dealing with resilience, it is important to define “resilience to whom” and “resilience of what” (Cutter, 2016 p.1). Accordingly, livelihood resilience as the building block of this study is conceptualized as “the capacity of all people across generations to sustain and improve their livelihood opportunities and well-being despite environmental, economic, social, and political disturbances” (Tanner et al., 2015 p.1). However, one of the main deficiencies in the literature so far has been the failure to identify the root causes of vulnerability as an initial step to understanding resilience owing to disciplinary perspectives and focus limited dimensions (Cutter, 2016). This in turn resulted in lack of working definitions, key indicators, and valid measurements for the concepts of vulnerability and resilience in the literature (Alfani et al., 2015; Bahadur et al., 2015; Razafindrabe et al., 2015; Cutter, 2016).

Most studies conducted on natural disasters and their effects on peoples’ livelihoods in different parts of Ethiopia focused mainly on drought and overlooked flooding and its impacts (Woldemariam, 1986; Rahmato, 1991; Sharp et al., 2003; Rahmato, 2007). The few available studies on floods also focus on issues such as risk perceptions and risk management strategies (Moges, 1978; Bekele, 2003; WMO, 2003; Nederveen et al., 2011). Although there are recent studies that looked into resilience and vulnerability in Ethiopia, flooding and its impact on livelihoods has not been investigated (Deressa et al., 2008; Simane et al., 2014; Mengistu et al., 2015). This is a key gap in the existing empirical studies given that flooding is a major natural hazard that affects the livelihoods of thousands of smallholder farming communities every year across the country (see also Table 2).

This study therefore addresses the gap in the literature by looking into the root causes of vulnerability and measuring livelihood resilience of smallholder farmers to flood hazards. Linking livelihood approaches to resilience thinking is imperative to enhance the understanding of livelihood dynamics and to explore how households maintain and improve their livelihoods in the face of natural disasters (Scoones, 2009; Sallu et al., 2010). In view of this, the study contributes to the disaster risk reduction literature by providing empirical evidences on the determinants of vulnerability and resilience to the recurring flood hazards. The study also adds to the conceptual and methodological debates surrounding vulnerability and resilience by focusing on the least studied hazard in Ethiopia and developing and applying context-specific indices. This would further contribute to the application of relevant measurements in relation to capturing the multidimensional nature of both vulnerability and resilience. Finally, the study highlights the synergy between the vulnerability and resilience¹, which need to be fostered, if the objective of achieving Sustainable Development Goals (SDGs) in rural parts of developing countries is to be addressed in years to come (Fig. 1).

Fig. 1

Location of the study district The map shows Dembia district of the Amhara region, Northwestern Ethiopia. It is located at 12°18'30''N and 37°17'30''E (see Fig. 1). It has an area of the 148,968 ha from which plain land accounts for about 87%, mountain and hills 5%, valleys and gorges 4.8% and water bodies 3.2%. The altitude of the district ranges from 1850 to 2000 m.a.s.l. Therefore, it is predominantly classified as Mid-land agro-ecology and the slope ranges from 2 to 4%. The district on average receives an annual rainfall between 700 mm to 1160 mm. Belg (the short rains February-April) and Meher (the long rains June-September). The average yearly minimum and maximum temperature is 18 °C and 28 °C respectively. Based on the recent Central Statistical Authority’s (CSA) population projection, the district had an estimated total population of 307,967 (CSA, 2013). Out of this total population, the majority, about 90%, are rural residents with an average agricultural household size of six persons. Source: Authors’ based on Ethio-Geographic Information System (GIS) and (CSA, 2007)

Methods

Research design

A quantitative-dominant, qualitative mixed research design was employed, where the quantitative data and qualitative information were collected concurrently. This approach helped the study to assess how vulnerability and resilience are conceived in local contexts, examine locally-specific impacts of flooding, and factors that shape the resilience of households in the face of this disaster.

Data sources

Quantitative data and qualitative information for this study were obtained from both primary and secondary sources. A cross-sectional survey of 284 farm households was supplemented by qualitative information from 12 Key Informant Interviews (KIIs), two Focus Group Discussions (FGDs), field observations, and Participatory Rural Appraisal (PRA) tools including problem ranking and scoring exercises. These data were obtained between March-May, 2015.

Sampling and sample size

In selecting the sample households for the survey, a multistage sampling procedure was employed. In stage one, eight Kebeles ² were selected from the 40 rural Kebeles in the district purposively as they are frequently hit by seasonal flooding. In stage two, two Kebeles (Tana Weyna and Gur-Amba) out of the eight flood prone Kebeles were selected purposively using pre-defined criteria. The criteria include, the physical proximity to flood hazard source particularly to the nearby rivers (location and exposure) and the severity and frequency of flood-disasters.³ After selecting the two Kebeles, a list of the households in 26 villages (15 in Tana Weyna and 11 in Gura-Amba) was recompiled and used as a sampling frame to select the households. Thus, a final sample of 256 households out of the 971 households were selected using systematic random sampling technique.⁴

For the qualitative interviews, both KIIs and FGD participants were selected purposively using criteria that includes being born in a particular village or lived there for not less than two decades; have a first-hand experience of flood disasters; and being knowledgeable about the local environment, weather patterns and climate. This was meant to capture the spatio-temporal perspectives of the studied households and communities about flood disasters based on recall.

Data collection instruments

A structured survey questionnaire was designed and piloted in order to generate information on households’ socio-economic and demographic characteristics, livelihood asset profiles, livelihood activities, and income portfolios. The questionnaire also consisted questions related to households’ vulnerability situations, including indicators relating to exposure, sensitivity, and adaptive capacity. Moreover, questions pertaining to absorptive and transformative capacities of resilience were added while adaptive capacity indicators were used as common indicators for both vulnerability and resilience. Both interview guides and discussion checklists were designed to gather qualitative information to supplement the household survey. Smallholder farmers, community members, government and non-governmental organization representatives, and leaders of Community Based Organizations (CBOs) were considered as key informants and FGD participants. Accordingly, 12 KIIs, two mixed FGDs consisting of 20 people (12 men and eight women), and two PRA exercises were carried out with the same FGD participants.⁵

Approaches to measuring vulnerability and resilience

In terms of measurement, Deressa and Hassan (2009) documented the two commonly used approaches (i.e., econometric and indicator based) to measure vulnerability to disasters, including flooding. In the earlier case, the use of econometric method such as regression analysis is commonly employed to construct the Livelihood Vulnerability Index (hereafter referred to as LVI). The drawback of this technique is, however, the challenge associated with testing various econometric assumptions concerning the standard errors, hypotheses, confidence intervals and imputing causality without making stringent assumptions (Etwire et al., 2013). In the latter case, it involves the selection of indicators that the researcher finds to largely account for the vulnerability (Deressa and Hassan, 2009). In this approach, the subjectivity of the variable selection process is considered as a limitation (Etwire et al., 2013). Although this is a major limitation of the indicator based approach, recently different scholars used this approach to construct LVI in different contexts, including Ethiopia (Etwire et al., 2013; Limsakul et al., 2014; Madhuri et al., 2014; Simane et al., 2014). Similarly, this study adapted indicator based approach to develop LVI of smallholder farm households in the study district.

LVI developed by Hahn et al. (2009) was applied to assess the vulnerability of households in the study area. The LVI measurement largely fits to the study context and target population (i.e., smallholder communities in sub Saharan Africa) and similar sample size based on primary data obtained through a cross-sectional survey. The LVI also helps to capture the key factors that reflect the vulnerability situation of smallholder farming communities in the face climate induced environmental hazards. Similar to the LVI used in Hahn et al. (2009), this study employed seven key variables, which relate to socio-demographic characteristics (SDC) (household size, dependency ratio, age, gender of household head and education), livelihood strategies (LS), health status (HS), food security status (FSS), access to water (AW), social network (SN), and flood disaster (FD) and its impact. Moreover, following Madhuri et al., (2014) and in line with the Sustainable Livelihood Framework (SLF)⁶ (Birkmann, 2006; Scoones, 2009) this study further included natural capital (NC) that mainly refers to ownership of land and size of farmland.

Calculating the LVI

The dimensions of vulnerability were systematically combined with equal weights to create an index on a scale of 0 to 1. As in the case of the computation of the life expectancy index of the Human Development Index (HDI), the computation of each indicator of the vulnerability index followed the process of standardization (Hahn et al., 2009).

$$ {I}_a=\frac{S_a-{S}_{\min }}{S_{\max }-{S}_{\min }} $$

(1)

Where, I _a is the standardized value of each indicator. S _a the original sub-component for household a, S _min is the minimum value of the indicator across all households, and S _max is the maximum value of the indicator across all households. After each indicator was standardized, the average value of each component was calculated using equation 2:

$$ {M}_a=\frac{\sum_{a=1}^n{I}_{a^i}}{n} $$

(2)

Where M _a is the one of the eight components for household a, ${I}_{a^i}$ indicates the sub-components indexed by i, which builds each major component, and n is the number of sub-components of each major component. After obtaining values for each of the eight components, the household level LVI was obtained by combining these components using equation 3:

$$ L V{I}_a=\frac{\sum_{i=1}^8{w}_{M_i}{M}_{a^i}}{\sum_{i=1}^8{w}_{M_i}} $$

(3)

Which can be further expressed as:

$$ L V{I}_a=\frac{w_{S D C} S D{C}_a+{w}_{LS} L{S}_a+{w}_{HS} H{S}_a+{w}_{FSS} F S{S}_a+{w}_{AW} A{W}_a+{w}_{S N} S{N}_a+{w}_{FD} F{D}_a+{w}_{N C} N{C}_a}{w_{S D C}+{w}_{LS}+{w}_{HS}+{w}_{FSS}+{w}_{AW}+{w}_{S N}+{w}_{FD}+{w}_{N C}} $$

(4)

Where LVI _a , is the Livelihood Vulnerability Index for household a, which equals the weighted average of eight major components, ${w}_{M_i}$.The weights of each major component are given by the number sub-component that make up each major component, which are used to guarantee that all sub-components have equal contribution to the total LVI (Sullivan, 2002; Hahn et al., 2009). The LVI value ranges between 0 and 1, where 0 denotes the least vulnerable while 1 implies the most vulnerable (Etwire et al., 2013; Madhuri et al., 2014).

Resilience is a multidimensional concept that blends relevant evidence as to how people really withstand shocks (Almedom, 2009). Though the concept of resilience has been popular in development studies including, poverty, vulnerability, and food security, it has been challenging to find a sound measure to resilience and how to quantify resilience remains controversial (Alfani et al., 2015; Béné et al., 2016). However, some empirical studies have attempted to measure resilience using a composite index as proxy indicator (Amaya, 2014; Alfani et al., 2015; Alinovi et al., 2015; Béné et al., 2016; Smith et al., 2015). The current understanding of the resilience entails three interrelated capacities (adaptive, absorptive, and transformative), which are relevant to its measurement (Amaya, 2014; Frankenberger et al., 2014; Bahadur et al., 2015; Béné et al., 2016).

Resilience being a context-specific concept, the dimensions and indicators may change depending on the context. In assessing resilience to flood disasters, most studies use ex-post resilience indicators as opposed to ex ante measurements partly because the debate in the resilience literature regarding the possibility of measuring resilience in the absence of a hazardous event is unsettled (Keating et al., 2014). Therefore, the SLF was adapted and built a resilience index using five capacity dimensions: social, economic, institutional, infrastructure, and community capacities with each having specific indicators. These indicators are then aggregated by equal weighting into the three components–adaptive, absorptive, and transformative capacitates to obtain a multidimensional livelihood resilience index (LRI), following similar steps used in the LVI computation as given by equations 1 to 4 (Amaya, 2014; Frankenberger et al., 2014; Suman, 2014; Smith et al., 2015).⁷ Thus, LRI constructed is expressed as:

$$ L R{I}_a= f\left( A{C}_a, AB{C}_a, T{C}_a\right) $$

(5)

Where,

LRI _a is the resilience index for household a

AC _a is adaptive capacity for household a

ABC _a is absorptive capacity for household a

TC _a is transformative capacity for household a

Using the FAO’s Resilience Index Measurement and Analysis (RIMA) model⁸ (Food and Agricultural Organization [FAO], 2012; Alinovi et al., 2015) equation 5 can be further expressed as:

$$ L R{I}_a= f\left( IF{A}_a, A B{S}_a,{A}_a, SS{N}_a,{S}_a, A{C}_a\right) $$

(6)

Where:

IFA refers to income and food access; ABS = access to basic services;

A = assets; SSN = social safety nets; S = stability; AC = adaptive capacity. Since the indicators used in RIMA have been applied to measure household’s resilience capacity to food insecurity (FAO, 2012; Alinovi et al., 2015), in this study, the RIMA components were contextualized and subsumed to into the three resilience capacity indicators to measure households’ resilience to flood disasters. Accordingly, IFA, A, and AC indicators were taken as part of adaptive capacity along with other indicators; S was captured under absorptive capacity indicators using sensitivity to flood disasters as a proxy indictor in addition to others; and SSN and ABS were included under transformative capacity⁹.

As this index was a rough approximation of resilience and scale-sensitive, which may not be useful for inter-household comparative analysis, a composite index using Principal Component Analysis (PCA) was constructed. PCA is a multivariate statistical technique mostly used for data reduction (i.e., larger number of variables into smaller numbers of components) and express the data as a set of new orthogonal variables called principal components (PCs) (Abdi and Williams, 2010; Abson et al., 2012; Schürer and Penkova, 2015). In this study, PCA was used both for data reduction and identification of the dominant factors that explain household’s resilience to flood disasters.

There are number of ways that can be used to retain principal component score. In order to obtain PCs, the study used Kaiser criterion of extracting factors with eigenvalues greater than one, which is one of the frequently used technique (Abdi and Williams, 2010; Mooi and Sarstedt, 2011; Abson et al., 2012; Schürer and Penkova, 2015). Thus, the heaviest loading of principal component expressed in terms of the variables as an index for each household that captured largest amount of information (Abson et al., 2012). The individual resilience score using PCA was computed using equation 7 as follows:

$$ R{S}_a={f}_1 X\left({a}_{a1}-{a}_1\right)/\left({s}_1\right)+\dots \dots +{f}_N\left({a}_{a N}-{a}_N\right)/\left({s}_N\right) $$

(7)

Where RS _a is the resilience score for household a;

f ₁ is the component loading generated by PCA for the first variable;

a _a1 is the a ^th household’s value for the first variable;

a ₁ and s ₁ are the mean and standard deviation respectively of the first variable overall the households.

After extracting the principal components, a simple linear regression was applied to check the relationship between resilience and vulnerability as used in a similar study (Madhuri et al., 2014). Apart from this, following Nguyen and James (2013) a dichotomous response items were used to capture subjective indicators of household resilience to flooding. These indicators were quantified and integrated by using an exploratory factor analysis (Costello and Osborne, 2005; Child, 2006; Preacher et al., 2013).¹⁰

Results and discussions

The nature of flooding and effects on livelihoods

Natural hazards such as floods and droughts often expose poor communities to vulnerabilities that can be investigated from two dimensions (1) external dimensions or vulnerability context which can be expressed as the exposure to circumstances beyond people’s control, including shocks, trends and seasonality (2) internal dimensions which refers mainly to socio-economic systems, access and use of resources to the extent to which peoples’ livelihood is affected by the exposure to external factors (Blaikie et al., 2014; IFRCS, 2015).

In view of this therefore, the nature of flooding in the study area in terms of its cause, magnitude, severity, frequency and duration is discussed as a major component of the vulnerability context of people. Alongside this, by drawing together the findings from the household survey, the FGDs and the interviews with key informants on the effects of flooding on the livelihoods of people is discussed with the perceptions of people towards flooding as a livelihood threat.

Flooding in Dembia district is a seasonal phenomenon. The district is situated bordering the biggest lake in Ethiopia–Lake Tana. Several rivers that spring from neighboring districts drain into Lake Tana traversing the district. According to the information obtained from the district Disasters Prevention and Preparedness Desk, the major cause of flooding in the area can be attributed to the over-flow of five major rivers namely, Megech, Derema, Nededit, Gumara, and Senzelit during the rainy seasons. According to key informants, these rivers reach at peak flows in the main rainy season starting from July through August with water volume showing declines only in late September. As a result, the rivers regularly inundate many nearby villages with water staying on the plains for several weeks. However, some severe floods have occurred in the past that are associated with heavy rainfall in the highlands. For instance, the floods of 1995/96, 2001, and 2006 were mentioned by FGD participants as the most severe flood disasters. Secondary records obtained from DPPA corroborate this information and show that severe floods also occurred much earlier in 1973/74 and 1982/83 in the district (DPPC, 1997a).

A change in the severity of floods was also noted by experts and other study participants. People felt that flooding is more severe and frequent than in the past. Most of them came to understand that the population pressure and the associated farmland expansion have brought people close to the rivers which made them more vulnerable to flooding. This view partly agrees with the major assertion in the literature which relates to causes of people’s vulnerability both to socio-economic and contextual factors compared to the mere exposure to floods (Handmer, 2003; Cannon, 2006).

In contrast, some participants stated that rivers have begun inundating farmlands and villages by changing their natural courses. For instance, one expert mentioned Megech River as one of such rivers that have changed its natural course since the 2006 flooding. The river (Megech) is now flowing in a new channel which is too narrow and shallow, causing the river to meander and spread out onto the plains easily overflowing its bank, flooding several villages in Tana Weyna Kebele.

Two points stand out from the above findings, (1) riverine flooding is the major type of flood in the study area (2) the nature of the flooding in the area is showing a marked change in terms of its severity having major consequences on the lives and livelihoods of people in the area. This finding is consistent with evidences from other studies in Ethiopia that suggest increasing frequency of flood hazards. In this regard, Maxwell et al. (2013) in their study of Tsaeda Amba district in Tigray (Northern Ethiopia) find that there is an increasing tendency of run-off and flooding due to environmental degradation. Similarly, a study by Tesso et al. (2012) indicates frequent flooding as a major environmental hazard that erode the coping capacities used by vulnerable communities such as kinship support network in North Shewa Zone of Oromia region. Focusing on riverine floods, a recent study by Hallegatte et al. (2016) that assessed the socioeconomic resilience to floods in 90 countries also found that, for poor people, a major risk associated with flood hazards is the loss of wellbeing. Other factors that contribute to and aggravate the flooding in the area were also revealed by FGDs and key informant interviews. The soil type of the district was mentioned as one such factor. According to informants from the district Agriculture and Rural Development Office, the black clay soil [which is the dominant soil type in the district] aggravates flooding as it is poor in its drainage capacity and gets saturated and sticky with even a small amount of rainfall. It also fails to absorb additional water flowing from rivers, contributing to flooding and water logging.

Although the nature of the watershed and soil type in the area can be mentioned as factors that influence the occurrence of flooding in the district, it is hardly possible to attribute the cause and the occurrence of flooding only to these factors. In fact, all of the district agricultural experts interviewed about the cause of flooding mentioned that flooding in the district is partly attributable to the following human activities that played a greater role in determining flood damage.

• 1. Deforestation: This made the highlands barren by exposing the top soil to heavy erosion and increasing the run-off of rain water from these areas to low areas. Periodic changes in the amount and intensity of rainfall aided by the lack of vegetation cover in the highlands also help in aggravating the run-off and the flooding in the study area.

• 2. Traditional and subsistence-oriented farming system in the highlands was mentioned as a factor that causes and accentuates the rate of soil erosion and run-off in the study area. According to the opinions of the district Agriculture and Rural Development experts, some irresponsible local farming practices such as tilling hilly lands have increased the problem of run-off and thereby contributed to increase flooding in low lying areas.

• 3. Lack of integrated conservation activities and watershed management was also mentioned as contributing factor to the rise in the frequency of flooding as well as the increasing human vulnerability in the area.

In general, the district’s geographic location, topography and soil type aggravated by the effects of human intervention such as deforestation, traditional cultivation practices and lack of sustainable water-shed measures were found to cause or exacerbate flooding in the study villages.

Effects of flood disaster on livelihoods

Flooding has been affecting the study villages for years. According to the district agriculture and rural development office, the study villages experienced one of the worst floods in 2001 caused by the heavy rainfall in the highlands that increased the volume of Lake Tana and the tributary rivers sending huge amounts of water into the nearby plains and beyond. As a result, thousands have lost their assets and were dislocated from their homesteads. Flooding has shown an increase in its intensity in the flood prone villages since then particularly after the river Megech has changed its course and begun flowing in a shallow bank crossing major settlement areas, farm and grazing lands.

The findings from the household survey indicate that crop damage is most the common type of economic loss experienced by households in the study villages. Accordingly, nearly all surveyed households (98.3%) reported that they have experienced loss of crops due to flooding in the last five years before the survey. Through the problem ranking and scoring exercises, participants of the FGDs also indicated that crop damage is the foremost impact of flooding in economic terms. The loss of standing crops such as teff was substantial during the floods in 2006 and 2009. During the FGDs in both villages, it was noted that farmers were compelled to change the cropping pattern from teff and wheat in to finger millet in recent years. In addition, almost all participants and key informants indicated that farmers in the study villages have begun to rely more on secondary crops such as chick-peas, field peas, and faba beans and other leguminous crops which grow by using the residual moisture left in the soil in the dry seasons. However, the overall production of cereals and pulses has gone down in recent years owing to the loss of soil fertility as a result of sedimentation which creates suffocation to such crops. In addition, the humidity of the soil resulting from flooding creates a favorable condition for pests such as Cut Worm (Agnotis Segetum ) that reduces the productivity of the crops. In relation to this, one of the participants of FGDs in Tana Weyna Kebele disclosed that:

…flooding is making the cultivation of crops a challenging task. During the rainy season, it washes away crops that we grow spending so much labor and time and when we plant secondary crops, Korache [Cut-worm] destroys it.

The loss of primary crops and the declining productivity of secondary crops suggest that exposure to food insecurity is inevitable for the affected households. The effect of flooding on the food security of households is also amplified by the loss of production as a result of the time spent on recovery and rehabilitation in the aftermath of the flooding. Flooding has also increased the vulnerability of households to food insecurity as attested by the increasing relief grain requests made by the District Agricultural and Rural Development Office.

Households’ vulnerability as measured in LVI

The LVI that measures the vulnerability of households to flood disasters indicates that most households are highly vulnerable to flooding with a mean value being around 0.5. The LVI shows the inter-household differences in terms of exposure, sensitivity, and adaptive capacity. Accordingly, the major contributing factor to the high vulnerability of households to flooding in the study area is found to be exposure with a mean index value of 0.65 followed by sensitivity with a mean index value of 0.56 out of 1 (Fig. 2). Thus, most households are highly exposed to flooding and more sensitive to flood-related risks such as gully erosion resulting in the loss of both farm and pasture lands (see Fig. 3a). Studied households are also found to have relatively low adaptive capacity with a mean index of 0.53 out of 1. This implies that the studied households have limited capacities in terms of offsetting flood disasters by employing long-lasting methods such as constructing flood dykes, which is only reported to have been used by 31.08 percent of households (see Table 3). Instead, as field observation shows many households largely rely on coping strategies mainly plastering the basement of their huts with daub, which may not help to withstand more severe flood hazards, frequenting the area in recent years (see Fig. 3b). Moreover, data from the household survey highlights that other frequently employed coping strategies include changing crops (86.01%), relying on informal social transfers (83.89%), and borrowing seeds (80.93%) (see Table 3).

Fig. 2

The three components of vulnerability Source: Authors’ own construction from household survey (April 2015)

Fig. 3

a Gullies created by flooding. b House built with raised platform, plastered with mud to protect from floods. Source: Field observation in Debmia district (May 2015)

Table 3 Coping strategies for flood disasters

The results of qualitative interviews and discussions corroborated the findings from the LVI.

Accordingly, participants of FGDs mentioned that households with adequate labor can engage in dyke construction and timely drain their farmlands. Moreover, it was highlighted that such households are able to engage in both on-farm and off-farm activities and maintain their household income during times of extreme floods. However, the lack of access to alternative income earning activities in the district, coupled with the severity of the recent floods. These floods were mentioned to have adverse impacts on most farmers. Lack of human capital, particularly labor was reported to be a major factor that heightens households’ vulnerability situation.

Focus group discussants agreed that the degree of exposure to flooding is mainly determined by the physical proximity of farmlands and settlement areas (villages). Poor asset holdings mainly farmlands and oxen were reported to be sources of social vulnerability. In the FGDs and KIIs, it was repeatedly noted that physical exposure to floods (physical vulnerability) was the major factor that puts studied households’ livelihoods at risk. In view this, it was vividly indicated the “better-off” households in terms of asset holdings were highly affected by flood disaster, which resulted in to the loss of assets accumulated over time. The major floods that occurred in the 2006, 2008, and 2012 rainy seasons were mentioned as blatant examples of such phenomenon. This, however, does not mean that asset holding did not contribute to the resilience of households, it only confirms the fact that not all households in the study area were exposed to floods to the same extent and therefore were not affected in similar ways. This view strengthens the evidence that exposure to flood events is a necessary but not sufficient factor in determining the vulnerability of livelihoods. For instance, participants of FGDs in Tana Weyna Kebele, noted that the extent of flood damage on standing crops, depends more on the proximity of a farmland to the river Megech as opposed to the asset holding of the household. Accordingly, it was stated that households whose farmlands are located near to the river were exposed to more flood hazards both in the short and long rains.

To establish the relationship between the resilience and the vulnerability of households in the study area, Ordinary Least Square (OLS) regression was used with LVI as an explanatory variable and the resilience index obtained using PCA as a dependent variable.

The result shows that the LVI decreases livelihood resilience index by 6.73 points, statistically significant at less than 1%. The first component of the PCA, which captures the largest variability of the sub-components is considered for capturing the resilience of surveyed households, which is composed of adaptive, absorptive, and transformative capacities (Frankenberger et al., 2014; Béné et al., 2016; Smith et al., 2015). The first component indicates the dominance of adaptive capacity over other components. The relationship between the two indices is to be expected as resilience is often taken to be the flip side of vulnerability (IPCC, 2001; 2007). In this study, adaptive capacity was taken as joint component shared between the LRI and LVI indices, however, absorptive and transformative capacities as the other components of LRI that positively contribute towards households’ overall resilience status seems to be relegated as the PCA only extracts the first component– adaptive capacity. Therefore, we argue that the comparison between the two indices need further analysis that captures the multidimensionality of both vulnerability and resilience.

Households’ resilience capacity as measured by LRI

Relying on PCA, factors that have eigenvalue greater than 1 were chosen as resilience indicators. Accordingly, the results from the PCA indicate that five of the 13 components have higher than one eigenvalues and represent 62.7% of the total variance (Table 4 and Fig. 4). Most of these variables belong to adaptive capacity indicators and include household and demographic characteristics (age, household size, education, and supply of labor). Next to household and demographic characteristics, livelihood diversification, which mainly belongs to absorptive capacity, describes the resilience of households towards flood disasters in the study area.

Table 4 Principal components of resilience indicators of households

Fig. 4

Resilience spider diagram of the major components the LRI. Source: Authors’ own construction from household survey (April 2015)

Following Nguyen and James (2013) those factor scores with the highest eigenvalue were used as a dependent variable for further analysis in the exploratory multiple regression. The result indicates that human and natural capital endowments mainly education and land holding size as well as engagement in more diversified activities mainly trade seems to be positive and significant determinants of resilience of households (Table 5). Thus, those with higher educational levels and having relatively adequate farmlands are likely to have more resilience. Most importantly, engaging in trade as the highest form of diversified livelihood strategies is likely to increase LRI by 0.042 points, statistically significant at less than 1%.

Table 5 Exploratory OLS on factors that determine LRI

The factor analysis results on the dichotomous response items also show that three of the six statements express smallholders’ subjective resilience.¹¹ The first component represents 22.8% of the variance and relates to greater reliance on social networks that contributes to adaptive and absorptive capacities, for example in terms of borrowing seeds (Table 6). Here, crop damage being the most common type of economic loss experienced by households in the study villages reflects the crucial importance of social capital in a household’s resilience.

Table 6 Principal components/correlation of dichotomous response items

At the time of disasters and soon after, people largely count on their kinship networks, mutual aid, self-help groups and indigenous organizations secure help and support (Haines et al., 1996; Aldrich, 2012). However, as the frequency and severity of co-variate shocks such as flooding increases, the role of social networks begins to wane. This process came out in the FGDs where participants have mentioned the severity of flooding in recent years as the main obstacle for relying less on kinship networks and neighbors. Moreover, flooding has affected the majority people in neighboring villages so much so that it was impossible to rely on kinship networks. For instance, one key informant explained that since the heavy flooding of 2006, the frequency and severity of floods are increasing in all villages as a result of which households have to “rely on relief grains to sustain their lives”. This opinion was also verified by data obtained from the District Agriculture and Development Office that showed an increase in relief grain recipients.

In general, resilience was understood as a state of having strength to quickly recover from the damages caused by flooding. A key component of livelihood resilience for many participants of FGDs and key informants was articulated as the ability to regain pre-disaster level of living without sustaining crippling damage to household assets that could push people further into poverty.

Moreover, during the focus group discussions it was indicated that flooding as a livelihood problem does not affect households equally in the study villages. This implies that the resilience of households is understood more in relative terms which further indicate the need to set some locally specific indicators in order to differentiate households in terms of their level of resilience. In this regard, the FGDs made with farmers in the study villages yielded some useful locally specific indicators that helped to measure the level of resilience of households.

Accordingly, the participants identified the location of farmland, critical asset holdings such as a pair of oxen, the ability to draw help form relatives in other villages, and time taken to recover from the impact of the floods as some of the major indictors of the livelihood resilience of households faced with flood- disasters in the study villages (Table 7). The categories were also used in the household survey to differentiate sample heads of households roughly in to three groups namely, those with high resilience, those with medium resilience and households with poor resilience or more vulnerable to flooding. These three categories only show the level of resilience of households in comparative terms and do not necessarily signify clear boundaries as they are only used to facilitate the analysis process. In addition, they do not show some causes of vulnerability such as illnesses, divorces and similar idiosyncratic shocks that contribute to the weakening of resilience.

Table 7 Factors that affect the resilience of households and communities in the face of flooding in the study villages

Through FGDs and interviews, it was possible to identify major factors that limit the resilience and coping capacity of households in the face of flood disasters. Accordingly, participants and informants have identified a range of factors that determine the resilience of households, by focusing mainly on the major flood disasters that occurred in the study villages in the past ten years. Since the majority of factors relate with livelihood resources and access to them, attempt was made to assess the household livelihood situations by using a combination of qualitative and quantitative methods. Below, the major factors that determine the resilience of households are discussed.

Natural capital: land

In any rural community land is a basic productive resource, and access to it determines the wellbeing of a given livelihood. According to the findings of this study, however, farmland location, and fertility were indicated to be more important than a mere access to land in determining the resilience of households in the face of flood disasters. The FGDs and interviews made with the study households indicated that the qualities as well as the location of farmland are the key factors that limit or enhance the resilience of households to flood-induced shocks. In terms of location, the proximity of farmlands to rivers was mentioned to have a significant role in determining the vulnerability and resilience of households more than the size and fertility of farmlands. This finding was also supported by data obtained from the household survey, in which farmland ownership was not found to have a significant effect on the resilience of households as almost all of the households (92.8%) own farmlands and those who do not own their own land were found to be equally distributed among the respondents.

This however cannot be taken to mean that access to land does not have a role in determining the resilience of households. In fact, it could be argued that access to land may indirectly determine resilience. The detailed discussions with participants of FGDs and key informants also indicated that farmers with no land holdings are less resilient to the effects of flooding as compared to those who have land or can access land through various mechanisms. This, as mentioned by focus group discussants and informants, was to be expected since the landless would lose their income largely drawn from wage labor on farms of other farmers during flooding and are likely to be affected even by moderate flooding as they lose the daily wages they earn from certain activities like weeding. Most participants of the FGDs also noted shortage of farmland in their respective villages. This problem, according to an informant from the Dwaro, have forced farmers, particularly the young ones to encroach the wetlands found on the shores of Lake Tana for planting horticultural crops such as spices. This finding corroborates with results from other studies that reported small landholdings, land degradation, and population pressure as the major causes of vulnerability to disasters in other parts of Ethiopia (Rahmato, 2007; Tesso et al., 2012; Maxwell et al., 2013).

Economic capital: financial asset

Economic capital generally refers to the financial resources that, in times of shocks could be used to reduce vulnerability and enhance recovery (Mayunga, 2007). The major forms of economic resource that were identified by the study households as having direct influence on the resilience or coping capacity of households are discussed as follows.

Livestock holding

Focus group discussants in the two study villages have identified the size and type of livestock owned by a household as a factor that determines the resilience of households. According to the focus group discussants, households who own a large number of livestock tend to be more resilient to the effects of flooding as they use the animals as a buffer stock. This gave them the financial capacity to quickly regain their livelihood, as they would sell their livestock and use the money to buy seeds, rent-in farmlands for planting secondary crops when the flood waters recede.

An interesting insight is also gained from the FGDs regarding the type of livestock and its role in the resilience of the household. Accordingly, the participants of FGDs mentioned that possession of farm oxen often enhances the resilience of households, since it gives the advantage of draining flood water from farmlands so as to lessen crop damage or failure.

However, focus group discussion participants and key informants alike agreed that flooding, with increased volume of water and duration, affected livestock and reversed the situation in recent years, in which those with more livestock were affected the most, since they lost their livestock during the floods through drowning and in the aftermath through various diseases and lack of fodder, which in turn affected their productivity. In view of this one key informant said the following:

A decade ago, farmers in our village used to keep many cattle. In fact, some farmers used to own as much as 60 heads of cattle. Currently however we are having problems even to keep our farm oxen as the grazing fields are now covered with weeds and the cattle are starving as they no longer find those fine grasses that used to grow in the fields.

Access to credit

Access to credit services was the other form of financial capital, identified by household heads participated in the study, as having effect on the resilience of households.

According to the household survey 36.9 percent of the respondents were able to have access to credit. And out of these, only 24 percent of them were able to receive loans from formal rural credit services (Amhara Saving and Credit Institution[ASCI]). This indicates that there is lack of access to credit, which is crucial in helping households to quickly recover from the effects of flood-induced shocks to replace lost assets and income. During the FGDs and interviews, it was also mentioned that households with no oxen, land and other assets were excluded from receiving loans as they were unable to furnish collateral. In relation to this, a young informant from Tana Weyna Kebele disclosed: “we are not given credit; they [ASCI] only give it to household heads who own land”. This exacerbates their vulnerability to the effects of flood-induced shocks.

During the discussions, it was also indicated that those who have better access to credit were in a better position to withstand the aftermath shocks of flooding, as they can replace their lost assets. Participants of the FGD from the Gura Amba Kebele mentioned that there was good access to credit services as opposed to those in Tana Weyna Kebele. This difference in accessing credit could probably be explained by the differences in the degree of physical proximity to the main credit provider i.e. Amhara Saving and Credit Institution. Some informants from Tana Weyna Kebele have also asserted that credit service was not made available to farmers living in most villages as the staffs of ASCI avoid remote villages since there is a need to make frequent visits in attempting to ensure repayments.

Generally, it can be argued that those households with economic capital in the form of livestock and credit are in a better position to withstand and recover from the effects of flooding as such assets contribute to their resilience through creating more opportunities for livelihood diversification that enable households to manage and cope with flooding in more sustainable ways. Among those not having access to credit and economic assets, their resilience level is found to be very low. For instance, among the 130 households, who reported having no access to credit, only 9 (6.92 percent) were found to have LRI above 0.5. Similarly, all the of the landless households were found to be non-resilient (see Additional file 1: Table B). These results indicate the important role that these and similar economic assets play in determining the resilience capacities of rural communities.

The FGD participants in both villages mentioned that more resilient households have the capacity to engage in both on-farm and off-farm diversification activities and keep a relatively good stock of animals in neighboring districts that enables them to further off-set livelihood shocks during major flood disasters like that of the 2006, 2008, and 2012 kremet floods. Diversification of income sources is stressed in the literature as an important strategy of enhancing the resilience of vulnerable communities and it “stands as the primary measure of household vulnerability and resilience (Tesso et al., 2012 p 884; Nguyen and James, 2013). Thus, given the benefits of diversification, households that diversify their income sources are likely to build their resilience to flood disasters in the future.

Human capital

Human capital as referring to the level of education, health conditions and availability of skilled labor was repeatedly mentioned as an important factor that shape the resilience of households and communities to disaster-induced shocks in the literature (Adger, 2000; Mayunga, 2007). In this study, the availability of labor in the household was found to be the most important form of human capital that contribute to household resilience in the face of recurring floods.

The qualitative data obtained from interviews and FGDs have also indicated that the availability of labor in a household play a determining role in enhancing the resilience of households. For instance, in explaining the role of labor in household livelihood resilience an informant in Gura Amba Kebele noted that “a farmer with no asset can live by the sweat of his brow as long as he is healthy and capable to work”. This clearly shows the value of labor in in terms of determining the resilience capacity of households.

Table 8 provides a summary statistics of the responses of surveyed households with regards to exposure to flood hazards and loss of assets disaggregated by resilience status. As indicted in the Table, the resilient and non-resilient households provided more or less similar assessments on their loss due to flood hazards except for flood exposure. Further, looking at the educational status of households as one component of human capital that determines the resilience of households, the results from the survey showed that there the resilient groups are better than the non-resilient ones. However, this difference is not statistically significant as a two-sample t-test with equal variances gives a result of Pr (|T| > |t|) = 0.1455. Thus, the evidences from the household survey seems to concur with the qualitative information that underlines the importance of the degree of exposure to flood hazards and the associated human activities such as land use changes. The finding on the prominent role of exposure concurs with Doocy et al. (2013) that provides a historical review of flood events worldwide from 1980 to 2009 and asserts that human vulnerability to floods is increasing among other things, mainly due to population growth, urbanization, and land use changes.

Table 8 Reported exposure to floods and loss of assets due to flooding

The major components of the LRI for the studied households is provided in Table 9. As shown in the Table, the mean LRI for all households is 0.44, which is below the minimum threshold value–0.5. This indicates that most households are not resilient enough to in the face of the increasing flood hazards in the area. Moreover, from the sub-components of the LRI, one can see that the studied households seem to have relatively higher absorptive capacity than adaptive or transformative capacities, a further indication of their vulnerability.

Table 9 Components of livelihood resilience index (LRI)

With the view of providing a more illustrative representation of studied households’ resilience capacity, we constructed a quadrant following the Andersen and Cardona (2013). The quadrant represents income per capita on the x-axis and LRI on the y-axis. Households falling in the right side of the mean values include, rich, but not resilient groups, highly resilient, and extremely resilient groups (Fig. 5). Households in the left side of the threshold include, poor, but resilient, highly vulnerable, and extremely vulnerable groups. In terms of the y-axis, the quadrant construction was based on the mean value of LRI, which was aggregated and/or composed from adaptive capacity index, absorptive capacity index, and transformative capacity index. The LRI value ranges between 0.1-0.99 (the lowest being 0.18 and the highest value stands at 0.62). The quadrant below and above the mean and/or threshold value divide was based on 0.44 LRI value. The quadrant with the mean value above 0.44 consists of poor but resilient, highly resilient, and extremely resilient groups. While, the quadrant with the mean value below the mean includes, rich but not resilient, highly vulnerable, and extremely vulnerable groups. The average monthly income of households is about 10.26 USD, which reflects the level of poverty and depravation among the study communities as this would mean that the average daily income of households is only 0.34 USD. As can be shown from Fig. 5, even by taking this low income level as a threshold, 31.9% of households were found to be vulnerable. When roughly extrapolated to the district level using CSA (2013) figures, this proportion would mean that 88,417 people are vulnerable to flood hazards in the district out of the 277,170-rural population.

Fig. 5

Resilience typologies by income of households. Source: Authors’ own computation based on household survey (April 2015)

The above quadrant is informative in terms of offering data as to where to focus development intervention efforts. In this regard, it is imperative to invest on various livelihood resilience schemes that enhances the capacity of highly and extremely resilient groups while focusing on reducing the number of highly and extremely vulnerable groups. Apart from this, it is also important to work on empowering poor-but resilient households and rich but not resilience households. This is particularly important given the overwhelming evidence, which indicates the likelihood of a shift in the global pattern and intensity of flood hazards associated with climate change (Few, 2003).

Conclusions

Focusing mainly on the vulnerability and resilience of rural households in one of the flood prone areas in Ethiopia- Dembia district, the study attempted to show that the nature of flooding in the study area has markedly changed over the past decade. The floods have become more frequent and severe owing to a number of factors that derive from both climatic and topographic conditions such as, periodic changes in the amount of rainfall, the nature of watershed system and soil type of the area. In addition, certain human activities including deforestation, increased settlement on flood plains, and traditional systems of cultivation were found to aggravate flood hazards in the area.

The findings of the study highlight the importance of access and use of livelihood resources such as size of farmlands, access to income diversifying options, credit as well as ability to draw help from social networks in terms of determining the resilience of households facing frequent flood hazards. The scale and impact of the recent floods and lack of basic infrastructural and social facilities are also found to have hampered the use of robust coping strategies by affected communities and households.

Given the livelihood context of smallholder farming system in the studied area, which is highly vulnerable to environmental hazards and persistently challenged by population pressure and land degradation, it is highly likely that the size of farm land will remain to be a major determining factor of the resilience capacity of the studied households. Despite this, however, context specific institutional interventions such as the integrated use of both safety nets and cargo nets may off-set livelihood predicaments. The safety nets can be implemented in the form of public works that are relevant to minimizing exposure to the recurring flood hazards, particularly through construction and maintenance of flood dykes. The cargo nets can be put in place in the form of targeted microfinance, flood insurance schemes, or agricultural input subsidization. These interventions will strengthen both the absorptive and adaptive capacities of households and communities in the short-term while enhancing their transformative capacity in the long-term. These imply that policy should focus more on addressing the factors that expose people to flood disasters and shape their resilience, rather than focusing on short-term emergency responses, which seems to be the norm in much of the flood affected areas in Ethiopia.