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The influence of decreasing soil fertility on the economic

and political stability in Egypt

Source: (Crane, 2015)

Nienke de Visser 11067993

Maayke Thompson 11030062

Timo van den Berg 10801375

Mees van Milligen de Wit 11056967 Research Report

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1. Abstract

In this research an interdisciplinary research on the influence of soil degradation on the political and

economic stability in Egypt will be introduced. Both the aim and the purpose of this research will be

assessed by providing a theoretical framework in which relevant theories are explained. A problem

definition states that soil degrading processes in the Nile Delta are mainly driven by anthropogenic

forces both direct and indirectly (influence of natural trends). This problem statement has produced

a research question and subquestions (listed in the introduction). In order to prevent further

escalation of the problem, an integrated framework demonstrates the integration of research from

different disciplines in order to provide a framework for the formation of effective policy measures

that are necessary for the prevention of future soil degradation in Egypt. The proposed methodology

provides insight into the execution of the interdisciplinary research and the results explain the

prospect of a reinforcing relationship between continuing soil degrading processes and political and

economic stability in Egypt.

This literature report researched how soil degradation in the Nile River Delta impacts the economic

and political stability. Soil degradation is a large problem in Egypt and its processes are mainly driven

by anthropogenic forces both direct and indirectly (influence of natural trends). These causes are

covered by several scientific disciplines, in this case Earth Sciences, Political Science and Economics.

This interdisciplinary paper describes this problem using an integrated framework, on the basis of

the central concepts​soil fertility, political stability and economic stability. This framework can serve

as a tool for the different actors to obtain further understanding of the current processes that

influence soil fertility and stability. Evaluating the framework shows a reinforcing feedback loop

regarding the level of political and economic instability. The Nile delta might be approaching a

critical threshold, and beyond this threshold the system might not be able to self-organise

sufficiently in order to shift back into the old system. Effective legislation, sustainable land use and

reducing the gap between governmental institutions and farmers to find common ground is key in

finding a sustainable solution for the problems in the Nile delta. Further research is needed to find

this solution and to collect detailed data on how resources as water and soils are divided in the Nile

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2. Introduction

Egypt is a densely populated country and the population is not equally spread over the total land

area. In fact, 60 million people live on less than 4 percent ​of the land, almost exclusively in the Nile

Valley, Nile Delta and a few cities along the Northern coast (Kotb et al., 2000). The share per capita

of agricultural land is ca. 0,05 ha in Egypt, which is among the lowest in the world (FAO, 2005).

Furthermore, the Nile Delta is subsiding, largely attributable to reduced sediment load from the river

Nile due to the Aswan Dam and irrigation upstream, as well as geophysical subsidence ( ​Bohannon, J.

2010; ​Dumont & El-Shabrawy, 2007). As a result, in combination with sea level rise, seawater

intrudes the delta, causing salinization of soils and freshwater (Yates et al., 1998).

Considering these figures and the high population growth rate (​Awad & Zohry, 2005)​, it is

not surprising that pressure on the agricultural sector and its productivity keeps increasing. Loss of

fertile soil is one of the most common problems in the Nile delta and has affected almost the

complete delta (El-Gunidy, 1989​)​, as shown in Figure 1.

Figure 1. A map of the Nile delta which indicates the degree of salinization of soils, categorized by darker areas being non-saline to lighter areas being highly saline. Lighter boundary lines are catchment boundaries and dots are groundwater pump stations, adopted from El-Gunidy, 1989.

The Egyptian government has introduced multiple policies in order to prevent soil degradation (Kotb,

et al., 2000). However, solving the problem is complicated due to a malfunctioning authoritarian

regime that has brought about many challenges that change over time (Kawy & Ali., 2000).

The loss of fertile soil may also have serious consequences for the economy of Egypt. In 2013,

agriculture employed 29,2% of the labour force (CIA Factbook, 2013). It is feared that low overall

economic growth, combined with population growth and decreased land productivity will lead to

short-term consumption rather than long term investment (Yates et al., 1998). This might severely

harm the stability of the economic future of Egypt. It is relevant to examine how soil degradation will

influence the political and economic stability in Egypt, because it is of large essence that the

previously mentioned problems are being dealt with, as the Nile river and its fertile delta are of great

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As the issue of loss of soil fertility is affected by land use practices, natural trends, political and

economic policies that cause both damage and loss of soils, it is important to look at all of these

perspectives (Kotb et al., 2000). The loss of soil fertility meets the requirements to be qualified as a

‘complex system’ because it meets most of the stated properties of a complex system proposed by

Rammelt (lecture, 2017). Scientific research in an interdisciplinary manner is crucial to address this

topic to capture the complexity and broadness of the problem of soil degradation in the Nile Delta

and its consequences. Solely focussing on one scientific area will not cover all relationships, causes and consequences regarding the overexploitation of fertile soil in the Nile Delta.

The objective of the research is to assess the conditions and consequences of the

overexploitation of a finite resource such as fertile soil and thereby analysing the relation of political

and economic stability on soil degradation. Moreover, this report aims to present a framework of

the problem that can be used in future research on reducing overexploitation or for introducing new

policies that can help shift Egypt towards more economically viable and sustainable alternatives.

This paper will examine the following research question: ​how will soil degradation in the

Nile River Delta impact the economic and political stability in Egypt? In order to answer this research

question two sub-questions are formulated:​how is soil fertility affected in the Nile Delta ? and: How

does a decrease in soil fertility affect the stability in the Nile Delta?

The study will be structured as followed; firstly, a theoretical framework will define concepts

such as ​soil fertility​and​stability.​Second, a methodological section will include the operationalisation

and elaborate on the interdisciplinary integration of the research. The results section will provide the

findings of the the research and formulate an answer to the research question. The report will be

finalized with a conclusion and a discussion which will present specific recommendations for further

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2. Theoretical Framework

The theoretical framework explains different concepts from the different, scientific disciplines to find

overlaps and contrasts and thereby interlinking these concepts.

Soil fertility

Soil fertility is a complex concept that is still evolving as new research is conducted. For this research

however, the following definition is adopted from Karlen et al. (1997) as it is the most common

definition: ​"the capacity of a specific kind of soil to function, within natural or managed ecosystem

boundaries, to sustain plant and animal productivity, maintain or enhance water and air quality, and support human health and habitation”. ​As this concept is naturally a more earth science-related

concept, the definition by Karlen et al. also links the ecosystem services of soil to stability. If a

threshold (ecosystem boundary) is passed (Folke et al., 2010), when present trends linked to soil

degradation will continue in the Nile delta, it is evident that a soil is less able to provide maintenance

of livelihood, habitat and other services for the human population. This reduced ability to sustain the

population in the Nile delta in the future will decrease both the economic and political stability.

Economic stability

With regards to the concept of economic stability, the International Monetary Fund (IMF) has

published the definition that is currently leading and is the most followed by scientists and policy

makers:

Economic stability refers to avoiding economic and financial crises, large swings in economic activity, high inflation, and excessive volatility in foreign exchange and financial markets. Instability can increase uncertainty, discourage investment, impede economic growth and hurt living standards.[] The challenge for policymakers is to minimize instability in their own country and abroad without reducing the economy’s ability to improve living standards through rising productivity, employment, and sustainable growth ​(IMF Factsheet, 2017).

This definition stresses the importance of continuity of economic activity and the absence of

economic crises. In case of instability, a nation's economy does not function properly, which might

lead to economic distortions, thereby changing the economic situation for the worse.

Furthermore, this definition sets out a clear task for policymakers to strive for as little instability as

possible. This shows that in the view from the IMF, policymakers are the stakeholders that are

responsible for reducing economic instability, as they are the ones that are able to actively take

measures. In this case, these policy makers will mostly be the Egyptian government. However, their

ability to mitigate economic instability is closely connected to the functioning of the government.

Therefore, the concept of political stability will be discussed in the next paragraph.

With regards to Egypt, the Nile Delta is economically particularly important as it accounts for 60

percent of the agricultural land and 60 percent of the population in Egypt (Yates, 1998).

Furthermore, it hosts a number of highly populated cities, such as Alexandria, Port-Said, Rosetta and

Damietta (El-Raey, 1997). As for the rest of the country, desert and uninhabited land represent

about 95% of the total land area (Ghar et al., 2004). In 2013, agriculture employed 29,2% of the

labour force (CIA, 2013). At the same time, urbanisation is an inevitable process due to economic

development and rapid population growth, which still leads to a noticeable loss net loss of

agricultural land (Ghar et al., 2004). Apart from the current economic implications, such as increasing

land prices, future risks have also been assessed. In the scenarios of Milliman et al. (1989) losses

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to subsidence and dammed rivers. El-Raey (1997) expects severe economic losses due to subsidence and sea level rise as well, since this will reduce the available agricultural land considerable.

Political stability

In order to define the concept of political stability in Egypt it is important to understand how the

‘ruling’ authoritarian regime in Egypt has come into power and how this regime exercises this power.

The ‘ruling’ authoritarian regime in Egypt refers to the individuals who ‘exercise power’ for a certain

period of time. In Egypt, the regime usually consists of the president, his close family and a small

group of ‘elite’ including carefully selected party, intelligence and military officers (Kienle, 2001).

When coup leader Gamal Abdel Nasser became prime-minister in 1954 and president in

1956, he ruled unchallenged up until his death in 1970. Nasser’s regime was not beneficial for the

growing income inequality in Egypt and brought about the challenge of millions underemployed and

poor citizens who lived in economic insecurity (Levitsky & Way, 2005). After his death in September

1970, Nasser was succeeded by Vice-President Anwar al-Sadat. President Sadat’s regime came up with several open-door economic policies and increased economic liberalization. With Soviet funding, he completed the Aswan High Dam which had great impact on industry, irrigation and

agriculture in Egypt (Blaydes, 2010). In October 1981, President Sadat was assassinated by Islamic

extremist and succeeded by Vice-President Hosni Mubarak. President Mubarak imposed the State of

Emergency, restricting assembly, freedom of expression and political activity in Egypt. In early 2011,

the beginning of a period also known as ‘the Arab Spring’, anti-government demonstrations started

to occur in Egypt. President Mubarak was forced to step down and hand over power to the army

council. He went on trial in August 2011, charged with ordering the killing of demonstrators. In June

2012, Mohammed Morsi, a Muslim Brotherhood candidate, narrowly wins the presidential election

(Blaydes, 2010).

When looking at these important political events, it becomes clear that most policies that

are put forth by the ruling Egyptian regime represent a rational response to the challenges it was

facing. In a political system, there are several political actors involved that have different

assumptions, goals and aspirations. Political actors work to solve problems, resulting in a series of

short-term decisions that accumulate into a set of policies (Pierson, 2004). The relationship between

regime and state becomes complicated, due to the fact that the Egyptian state is large and has the

tendency to promote policies that contradict each other (Poggi, 1978).

The short timeline presented in the paragraphs above indicate that the political system in

Egypt has been far from stable in the last 60 years. Not only have successive regimes and state

leaders introduced policies that contradicted those of their predecessors, violent demonstrations

and even revolutions have made the evolution of political action in Egypt very unpredictable.

3. Methods

In order to conduct this research, the following methodology has been used. Data was gathered by

making use of secondary scientific sources. This implies that this information has been acquired by a

researcher and has been integrated in this study. Due to the limited availability of time and

resources was it not possible to collect primary data. For this research, both qualitative and

quantitative papers have been used. Acquiring the data has been done by studying and evaluating academic papers for an extensive period of time.

In sampling the data, there has been a focus on articles from scientific journals that have Egypt

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locations have been used as well, wherever it was useful to provide more context. With regards to

the origin of the cited researchers, data was gathered from both Egyptian researchers as well as

from non-Egyptian researchers. This choice has been made because on the one hand, Egyptian

researchers may have inside information about local practices and may be better able to interpret

their results in the right cultural context of Egypt. This could be valuable for the research. On the

other hand, researchers with a different origin might have the ability to evaluate Egyptian practices

and traditions from an outsider's perspective. This external view may be refreshing and therefore

contribute to the research. There has been tried to use to most recent data as possible, in order to

decrease the risk of data. However, in some cases it was useful to cite older papers, as the change

over time in certain doctrines was an addition for the research. This occurred for example for data

from the political science perspective. To understand several current phenomena, it is crucial to have

a basic understanding of the policy history of Egypt. This provides a justification for using older

secondary sources. In conclusion, the authors of this literature study have tried to keep data as

independent and diverse as possible.

The search strategy that has been applied can be divided in different phases: firstly, the different

disciplinary concepts have been studied separately, to achieve a basic understanding of the relevant

subjects. Secondly, the disciplinary definitions have been compared in order to find connections and

similarities. In order to cross this disciplinary boundaries, the search strategy has been expanded

towards merely interdisciplinary papers.

The analysis of the data follows a similar pathway. In the first phase, the source is being appraised by

assessing how the research has been performed, what its results are and how much it is cited by

other researchers. In the second phase, the fit with this research has been investigated. Papers that

contained context in line with this research made this research more convincing, whereas papers

that showed contrast with the rationale of this paper where reason to further research that topic.

By following this method, the authors were able to present a clear answer to the research question

in the results and conclusion.

3.1 Interdisciplinary Integration

In order to perform an interdisciplinary research, it is of importance to define both the linkages

between the involved disciplines and the conflicts that may rise by different approaches towards the

subject. The integration process takes place based on the analysed linkages, aiming to merge all

interdisciplinary lenses into one framework.

In order to analyse this complexity it is necessary to find ‘common ground’ between the different

disciplines. Repko (2016) clearly explains how ‘common ground’ can be formed in order to analyse

different conflicting disciplines in an interdisciplinary approach. Because this research focuses on the

influence of both soil fertility on the political and economic stability and the influence of the political

and economic stability on soil fertility it is of essence to find ‘common ground’ and approach this

problem from an interdisciplinary perspective.

Due to numerous involved disciplines and concepts in the Nile delta considering the soil

fertility problem, common ground between the different disciplinary insights have to be created in

order to integrate towards an interdisciplinary framework. As earlier stated, the integration

techniques provided by Repko (2016) will be used as a method to integrate the different disciplines

and form common ground. In this research, the ​extension​method by Repko (2016) is used to expand

the meaning of an idea beyond the domain of one (sub)discipline into the domain of another

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disciplines interlinks them. Consequently, the different causal links or relations between different

concepts can be mapped or arranged (Repko, 2016). The result of the process of this ​extension

method is visualised in figure 3.

Figure 3: Integrated framework, visualising the different disciplinary insights in one interdisciplinary framework. For this framework the extension method of Repko (2016) is used.

This integrated framework shows the interactions between the different disciplines. The most

important observation is the interconnectedness between the concepts, except for ​Sea level rise, ​all

concepts influence each other and therefore create reinforcing feedback loops. In the case of the

Nile delta, these reinforcing feedback loops have negative consequences for the stability of the

system. Reinforcing loops in general have the tendency to destabilize a system and might even shift

a system into another state. However, looking at it the other way around, it can be seen as an

opportunity because it causes a system to change (Meadows, 2008). The integrated framework will

be analysed in the results section of this research report. The different interconnections will be

explained and analysed, furthermore the meaning of these linkages will be presented.

Despite the fact that this integrated framework is an abstract view of the actual situation it gives

insight in the interaction between the different concepts and actors. With this framework it is

possible to answer the stated research questions and subquestions in an interdisciplinary approach.

Nevertheless, it should be noted that not all involved actors are studied and thus not incorporated in

this abstract integrated framework and therefore not all interactions are taken into account.

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7.1. How soil fertility is affected in the Nile delta

Because the problem of loss of soil fertility covers multiple disciplines, this problem exists of a large

number of interconnections between different elements of the system in the form of feedback loops

which for example influence several scientific disciplines.

The Aswan High Dam (AHD) has been named by various authors as a negative influence on the

availability of fertile soil in the Nile delta. It has altered the natural flow and sedimentation cycles

from the Nile, causing a disappearance of the annual floods in the Nile delta (Bohannon, 2010;

Stanley & Warne, 1998; Negm, 2017; ​Abd-El Monsef et al., 2015​).

The Nile delta is subsiding due to compaction of the clayey soils that once were deposited by the

river Nile (Stanley & Warne, 1993; 1998). This loss of land is not compensated anymore by sediment

from the Nile, because of the blocking of sediment by the Aswan High Dam. This means that arable

land is in a trend of disappearing into the sea, especially in relation to the projected sea level rise

and related increased coastal erosion. When the dam was constructed in 1960, it was seen as a

political project from Nasser, with comparisons between the dam and the building of the pyramids

to boost nation-building (​Van der Schalie, 1974). However, side-effects were mostly overlooked. The

increased subsidence due to the lack of sediment, in combination with projected sea level rise due to

the global warming theory and therefore increased coastal erosion, will further decrease the area of

arable land.

In addition to the increasing subsidence and sea level rise which lead to loss of soil availability and

fertility, poor land use practices by the periphery put even more pressure on the agricultural lands.

In the Nile delta, excessive irrigation, human intervention in natural drainage, improperly time use of

heavy machinery, poor water quality and the absence of conservation measurements are the key

processes causing loss of soil fertility in the Nile delta (El Baroudy, 2005; El Baroudy, 2011; El

Baroudy, 2014; Elewa & Nahry, 2008; El-Kway et al., 2011; Mohamed et al., 2013; Morgun & Kovda,

2011; Shalaby & Tateishi, 2007). These processes need to be defined in order to be applicable for

different stakeholders.

Conservation of water is closely related to excessive irrigation and is defined as the capacity to reuse

water. The reuse of water can be achieved through several water-saving methods. Compaction due

to heavy machinery is defined as the increase in bulk density due to increased pressure (g/cm ​3​)

(Mohamed et al., 2013). Water quality is measured by the electric conductivity (EC), temperature,

pH, ionic composition of major and trace components and total dissolved solids (TDS) (Masoud,

2014; Wahaab & Badawy, 2004) Lastly, poor human intervention in natural drainage systems can be

defined as the extent to which human negatively interfere with natural drainage systems and

thereby causing water logging which is measured in the height of the water table (Abdel-Dayem, &

El-Safty, 1993; El Baroudy, 2011). These processes are mostly used as a response to lower yields due

to decreased soil fertility (El Baroudy, 2011; Shalaby & Tateishi, 2007). Furthermore, these processes

are usually carried out to increase the amount of available water. At first hand these processes might

seem to be beneficial for farmers because of increased yields over a short period of time, however,

over a longer period of time these processes severely increase the loss of fertile soil and thereby

decreasing soil fertility and consequently decreasing yields (Kotb et al., 2000 )​. In addition to this, the

absence of floods from the river Nile due to the Aswan High Dam cause salinization and pollution of

soils in combination with the projected sea level rise. The delta is not ‘rinsed’ of polluted water

anymore due to floods and the increased water table leads to an increased evaporation. ​Pessarakli

& Szabolcs (1999) state, concerning the fertility of soils affected by increased salinity, that for

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lead to salt stress by plants, seriously hindering crop yield and growth. This further affects the fertility of soils in the Nile delta.

The periphery in the Nile delta was and still is heavily dependent on the same type of resource

namely, water and fertile soil. Therefore, little differentiation within the agricultural industry has

occurred. As a result, it can be argued that the periphery is currently in the social trap of path

dependency (Boonstra & de Boer, 2014). This means that the periphery counters the loss of soil

fertility with processes that eventually further increase loss of soil fertility. Path dependency might

even lead to reinforcing feedback loops (Boonstra & de Boer, 2014; Meadows, 2008).

Because the Nile delta is heavily dependent on fertile soil and water, multiple scholars researched

the past and current high rates of loss of soil fertility in the Nile delta (Elewa & Nahry, 2008; El-Kway

et al., 2011; Mohamed et al., 2013). Therefore, knowledge seems to be abundant. However, loss of

fertile soil is still increasing​ in the Nile Delta ​(​Mohamed, 2016).

In conclusion, multiple factors that decrease the fertility of soils in the Nile delta can be divided in

two main categories. The first category includes consequences for the fertility of soils due to the

altered water regime of the Nile river and the trend of rising sea levels. Subsidence, coastal erosion,

salinization and water logging tend to be examples of these negative consequences. Furthermore

the loss of fertile soil, incurred by the periphery in the Nile delta further diminishes the soil fertility

by excessive irrigation, intervening in the natural drainage system of the delta, improperly time use

of heavy machinery, poor water quality and the absence of conservation measurements.

One important actor in the system that causes the periphery to continue these poor agricultural land

use practices, further degrading the land to a point of adverse yields, is the Egyptian authoritarian

regime (Bush, 2007).

Figure 2: Location of the Aswan High Dam (AHD) in Egypt (Source: Heldal, T., n.d. Assessed on 21

November 2017, retrieved from: http://www.quarryscapes.no/images/Egypt_sites/aswan_loc.jpg ).

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President Nasser’s regime was not beneficial for the growing income inequality in Egypt and brought

about the challenge of millions underemployed and poor citizens who lived in economic insecurity

(Levitsky & Way, 2005). During Nasser’s rule, protests in Egypt’s peripheral regions occurred as a

reaction to changes in tenancy law that had kept Nasser’s reforms from giving rights and economic

security to land tenants and rural poor (Bush, 2007). Since 1987, small-scale farmers had repeatedly

suffered from market reforms, withdrawals of state guarantees, increased poverty,

misunderstanding over land boundaries and struggles with access to irrigations (Bush, 2007).

After his death in September 1970, Nasser was succeeded by Vice-President Anwar al-Sadat. President Sadat’s regime came up with several open-door economic policies and increased economic liberalization. With Soviet funding, he completed the Aswan High Dam which had great impact on

industry, irrigation and agriculture in Egypt (Blaydes, 2010), as mentioned earlier in the result section

of this paper. In October 1981, President Sadat was assassinated by Islamic extremists and

succeeded by vice-President Hosni Mubarak. Mubarak started to dismantle Nasser’s redistributive

reforms from the 1950’s and 1960’s, but his counter revolution only worsened rural poverty and

failed to raise agricultural productivity. Furthermore, Mubarak imposed the State of Emergency,

restricting assembly, freedom of expression and political activity in Egypt, making it hard for the

oppressed to express their dissent (Bush, 2010).

One of the most violent food riots and opposition to authoritarian governmental policies occurred in

2008. At this point, more than half of Egypt’s population was living below the poverty line. Egypt was

severely food insecure (Bush, 2010). Anger in peripheral regions over everyday struggles were

fuelled by price inflation. Farmer mobilization challenged the increasing privatization of land and

local inequality, but the opposition was very uneven (Bush, 2010). The food riot that occurred

offered a glimpse of responses from oppressed peripheral regions to failing policies created by the

authoritarian regime, which the government only countered with violence and palliatives of

temporary price controls. It almost seemed as if governments waited for the market to lose its

volatility because this was an easier practise than addressing issues of agricultural policies (Bush,

2010).

vIt is important to create a link between the failing policies created by powerful Egyptian

authoritarian regimes and the failing agricultural practices exercised by farmers in peripheral regions

that keep increasing the degradation of fertile soil in Egypt. A theory that can help to understand this

connection is the resource dependency theory which is based on the fact that power and resource

dependence are directly linked. Pfeffer & Salancik (1978) state that this linkage comes into being

because resources are a basis of power and actors depend on resources. As political or economic

environments contain several actors, resources required by one actor are often in the hands of other

actors. Originally independent actors can therefore be dependent of each other; actor A’s power

over actor B is equal to actor B’s dependence on actor A’s resources.

So how can the resource dependency theory and its core concept be applied to the Egyptian case of

declining fertile soil? Although the Nile River flows through Egyptian land, its water is considered to

be a scarce natural resource due to a rapidly growing population, a limited quota of Nile water and

to wide desert lands where main drinking and irrigation water originates from underground sources

(Afifi, 2009). More than 97 percent of Egypt’s freshwater emanates from the Nile of which it spends

86 percent on agriculture (Wiebe, 2001). Even though the country has the longest history of water

engineering and management in the world, Egypt is facing some key development challenges

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Like in in many other countries, the water crisis in Egypt affects the poorer regions, or

periphery, the most. Nearly 70 percent of the poor or food insecure people live in these peripheral

areas (Wiebe, 2001). Communities in these areas depend of the Nile for fertile soils (water, irrigation

for crops). One could state that the situation in Egypt is in line with concepts of the resource

dependency theory, which notes that resources flow from a ‘periphery’ of mostly poor and

underdeveloped regions to a ‘core’ of wealthier and developed regions (Bush, 2007). Peripheral

regions in Egypt are dependent on a resource of which the management is controlled by the current

governmental regime via policies that fit to their best interests. The resource fertile soil is handled by

uninformed and poor peripheral regions but the yield from the resource is controlled by the

government, which has resulted in severe economic distortions.

The discussed imperfect land and capital markets can also significantly influence the

decisions of farmers whether or not they will try to control soil erosion. Land prices are the most

reliable indicator that a farming household will have of the effects of soil erosion on land

productivity (Barbier, 1997). However, rural land markets are distorted by the governmental policies,

as discussed above. Consequently, the costs of soil erosion, in terms of future crop productivity and

income, may not be reflected in, or is not even related to the price of land (Barbier, 1997). As a

result, the lack of effective markets distorts the farmers decision as to whether an investment in soil

protection is worthwhile (Barbier, 1997). Furthermore, poverty clearly constraints farmers ability' to

manage soil fertility (Barbier, 1997). For a large group of small-scale farmers in Egypt, land

productivity, and therefore household income, is declining and there is limited access to capital

and/or alternative economic opportunities (Sowers, 2011).

Thus, farmers have the option (and sometimes do not even have the possibility to do so) to protect

the soil because of future productivity and income potential, even though this choice is not reflected

in the price of the land, or to exploit the soil for immediate gain today. This makes the opportunity

costs of soil conservation in Egypt extremely high (Barbier, 1997). As a result, due to economic

distortions, farmers do not have an incentive to improve their land use and to protect their soils.

Since the 1980's the Egyptian government has been taking strict measures in order to reduce the

pressure on agricultural land (Ghar et al., 2004). Legislation that prohibits appropriation of

agricultural land for urban purposes has been issued as well as land use legislation (Ghar et al.,

2004). However, Ghar et al. (2004) concluded after a land monitoring research that the urbanisation

process still has led to a noticeable net loss of agricultural land. Apparently, the government is not

able to protect the productive agricultural soils. Even more, Bohannon states in his paper published

in 2010 that environmental policies regarding water availability have little to no effect. Basically the

greatest power that the Egyptian government has, is the control of the influx of water into the Nile

delta (Stanley & Warne, 1998; Bohannon, 2010). But the key to effectively use that water for

agriculture in the Nile delta, lies in effective policy making in that specific area.

Assuming that farmers have the possibility to adjust their land use, Barbier (1997) argues that

several phenomena can affect the farmers perception of the costs and benefits of controlling soil

erosion. These are market, policy and institutional failures such as insecure tenure or ownership of

the land and distorted market prices for input and output (Barbier, 1997).

All of the above elements are present in the current economy of Egypt. As discussed above, Egypt

has a turbulent history of governmental involvement and reform policies. This also applies to the

tenure and ownership of land, where uncertainty about property relations accelerated migration from the countryside into the great cities (Malm & Esmailian, 2013).

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Furthermore, Egypt has a long tradition of governmental subsidies. During the period 2001-2011, more than 20 percent of total governmental expenditures were spent on subsidies.

(Ghoneim, 2012). A significant part of those are food subsidies. However, the food subsidy system is

put under pressure by inefficiencies, related to corruption, waste and lack of right targeting

(Ghoneim, 2012). Because the food subsidies make the state the largest buyer of wheat (about 30

percent of the wheat production), the Ministry of Social Solidarity is able to set the leading food

price (Malm & Esmailian, 2013). These practices have suffered greatly from corruption, as it turned

out that influential people had private companies that benefited from manipulating the prices of

wheat (Ghoneim, 2012). This is a clear example of both institutional failure as well as a distorted

market price for output and is an obstruction to a free and well-functioning market. In addition,

small scale farmers are often not able to manage. Now salinization is speeding up, farmers see their

harvests fail more often. As a way of coping, they pour sand on their land to elevate it (Malm &

Esmailian, 2013), change to rice cultivation (Bohannon, 2010) and pumping up groundwater (Stanley

& Warne, 1998;​El-Agha et al., 2017)​. But sand is the property of the owners of the land on which it

is found, which makes it a commodity in private hands; on the sand market, prices are constantly

rising (Malm & Esmalian, 2013). The lack of monitoring and effective regulation of groundwater and

surface water use (Bohannon, 2010;​El-Agha et al., 2017) ​also leads to a ‘tragedy of the commons’,

where farmers pump up water and use land elevation techniques, íf they have the resources,

creating serious problems for agriculture in the Nile delta in the long term. This creates a division

between farmers, the poorer farmers have to abandon their land, while those who stay are the ones

who can afford the sand (Malm & Esmalian, 2013). This distorts the free market even further.

In conclusion, the market distortions, mainly caused by government policies affect economic

stability. The Nile Delta is of high importance for the agricultural economy of Egypt. Therefore,

declining productivity due to soil degradation obviously has negative consequences on the economic

stability. In the earlier discussed definition of economic stability, policymakers are held responsible

for economic stability. In this case, the Egyptian government has the difficult task to reduce economic distortions in order to reduce soil degradation.

​7.2 How a decrease in soil fertility and political and economic stability impact one another

The relationships between all concepts have been illustrated in the integrated framework (figure 3).

The arrows show the causal connections. When taking the relationships illustrated in the integrated

framework into account, the structure and presentation of the results can be anticipated as

followed: the two main actors, being the government (policies) and farmers in peripheral regions

(cultivation), both (in)directly contribute to poor agricultural practices. These poor agricultural

practices together with factors such as sea level rise and enhanced subsidence due to sediment

blockage by the AHD, account for almost all loss of fertile soil.

Moreover, malfunctioning governmental policies regarding the agricultural sector and poor

agricultural practices executed by farmers in rural areas therefore (in)directly lead to economic

distortions which in turn puts more pressure of the government and the farmers and thus, leads to

an even greater loss of fertile soil. From both the results in paragraph 6.1 and the integrated

framework, it becomes clear that multiple feedback loops occur; forcing the entire system to keep

reinforcing itself.

Distance and a lack of communication between the government and peripheral regions lead to a

continuous loss of fertile soil, which in turn leads to more political malfunctioning and more detachment between the government and the periphery. This phenomenon can be explained as followed; when state institutions are weak and budget procedures lack transparency, resource

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dependent countries tend to undermine democratic governance and generate authoritarian governments (Wantchekon, 2002). According to Dahl (1971), an uneven distribution/a lack of/a

declining stock of resources can push actors to try and influence the behaviour of actors that are in

grand possession of the required resources. Furthermore, extreme inequalities in the distribution of

key resources often go with similar inequalities in political resources. In other words, a country with

extreme inequalities in resources stands a very high chance of having extreme inequality in the

exercise of power and hence to an authoritarian regime. It is often these authoritarian regimes that

incite the opposition (peripheral citizenry) to resort to political violence in competing for political

power and thereby generating political instability (Wantchekon, 2002). Taking this into account, the

complexity of the problem can be simplified, which can help to clarify the interconnectedness of the

illustrated concepts. A potential limitation of this structure can be that other influential factors may

be overlooked. However, these factors are likely to fall outside the scope of our disciplines and

thereby outside the scope of our research, or are too large and/or complex to fit within our system

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8.​ ​Conclusion, discussion and recommendations

This paper has examined the following research question; how will soil fertility in the Nile River Delta

impact the economic and political stability in Egypt? Sea level rise, subsidence and poor human land

practices are the processes leading to severe loss of soil fertility in the Nile delta region. These

processes decrease both political and economic stability by increasing the gap between the

periphery and the authoritarian governmental regime. It is evident that continuous soil degrading

practises will indeed impact the future development of political and economic stability. However,

the answer to this question is far from unambiguous and needs more, elaborate research to provide

a relevant framework for stakeholders to sustain the future of the Nile delta. In the process of this

research it became clear that the current level of political and economic instability will in turn impact

the ongoing phenomenon of loss of soil fertility. This reinforcing feedback loop might have a

disastrous effect on all involved actors because it has the potential to further destabilize the system

shifting the system towards a new stable state where salinization and infertile soils make it

impossible for the large population that depends on agriculture to sustain. The Nile delta might be

approaching a critical threshold, and beyond this threshold the system might not be able to

self-organise sufficiently in order to shift back into the old system. In order to break these reinforcing

and recurring phenomenons, action by different actors is needed. However, this research recognizes

Egyptian governmental institutes as the actor with the most power considering soil fertility (and

inherently fresh water) as resources, knowledge and legislation and might therefore be the key in

breaking this feedback loop. Effective legislation, sustainable land use and reducing the gap between

governmental institutions and farmers to find common ground is key in finding a sustainable solution

for the problems in the Nile delta. It is relevant for further research to find this solution and to

collect detailed data on how resources as water and soils are divided in the Nile delta among farmers

and to gather specific, quantitative data on water use, salinization and land use and to structurize

this data for effective policy making.

The provided interdisciplinary framework can serve as a tool for the different actors to obtain

further understanding of the current processes that influence soil fertility and stability.

Consequently, these actors might be able to collaborate in order to cope with the increasing soil

degradation. As earlier stated in the interdisciplinary integration, not all actors are taken into account and therefore the integrated framework is a simplified model.

In this research only a small part of the complexity of the problem of soil fertility in the Nile Delta is

analyzed. Earth science, economics and political science are used as a basis for this interdisciplinary

literature review. However, there are more disciplines involved in this problem which can play an

important role in revealing and clarifying certain feedback loops such as social sciences and human

geography to identify key factors in population dynamics in the region and where to effectively

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