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Coastal Landscape between

Resistance and Resilience to Sea

Level Rise

Lobna Mitkees

2013

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Abstract:

Climate change is expected to affect considerably the coastal communities in

specific, through the coming century. Sea Level Rise will be one of the greatest

challenges that will confront the coastal region. This will be associated by

increase in the flooding risk, coastal erosion, and increase in storm surges, so as

many other climatic events. Coastal communities in the Egyptian Nile Delta are

highly vulnerable to the threat of SLR, given that the vulnerability is determined

by its social, institutional, economic capacity to respond to change.

The current paradigm in dealing with the coastal communities is towards

mitigating the impact and increasing protection measures. However this

arguably, establishes resistant coastal community on the account of its

resilience (Klein et al 1998). The current measures conducted to reduce coastal

hazards proved to increase vulnerability of the coastal communities. Hence, this

requires change in paradigm from conventional, protection thinking towards a

more holistic approach in coping with future threat.

Resilience is a new prominent paradigm that offers more flexibility in coping

with change. The term resilience has become a prominent topic that recently

emerged in dealing with changes and very much confined within the discourse

on climatic change. The resilience of a community, of its physical and built

environment, of its homes, buildings and built infrastructure, can be viewed as

its ability to withstand, and adapt to, the changing circumstances.

This will require understanding the natural environment and incorporating it

into the design process. Therefore, hazard can be viewed as a natural

phenomena rather than a threat in designing new coastal cities. The study will

present Alexandria as a resistance paradigm. Then will offer resilience measures

for the newly proposed City of New Motobus.

Keywords:

Sea Level Rise, Resistance, Resilience, Vulnerability, Hard –Soft measures,

Holistic approach

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Coastal Landscape between Resistance and Resilience to Sea Level Rise A Thesis submitted in the Partial Fulfillment

for the Requirement of the Degree of Master of Science

in Integrated Urbanism and Sustainable Design

by Lobna Mitkees

Supervised by Prof. Antje Stockman Professor of Landscape Planning and ecology University of Stuttgart

Prof. Mohamed Salheen Professor of Urban Planning and Design University of Ain Shams

Examiners Committee Title, Name & Affiliation Prof. (external examiner) Professor of (…) University of (…) Prof. (Title/Name) Professor of (…) University of (…) Prof. (Title/Name) Professor of (…) University of (…) Prof. (Title/Name) Professor of (…) University of (…)

MM/DD/YYYY

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Disclaimer This dissertation is submitted to Ain Shams University, Faculty of Engineering

and University of Stuttgart, Faculty of Architecture and Urban Planning

for the degree of Integrated Urbanism and Sustainable Design.

The work included in this thesis was carried out by the author in the Year 2013

The candidate confirms that the work submitted is his own and that appropriate

credit has been given where reference has been made to the work of others.

06/08/2013

Lobna Mitkees

Signature

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Acknowledgment:

I would like to express my sincere gratitude my IUSD professors and colleagues

respect to my advisors Prof. Mohamed Salheen , Prof. Jose Moro, Prof. Antje

Stockman, Phillip Misslives, Nina Gribat, Bernd Isenberg and Mona Mannoun

for their valuable insights and guidance that helped me throughout the IUSD

years.

Moreover, my greatest appreciation and friendship goes to the IUSD Team and

all my colleagues in Cairo and Stuttgart who have provided for the greatest

moral support during hard times of frustration witnessed while going through

this new academic experience.

Last but not least, I would like to thank my supportive family for their love and

faith in me, for that I would always be indebted to them.

.

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Table of Contents

List Of Figures ................................................................................................ xiv

List Of Tables ................................................................................................ xvii

Chapter 1 ........................................................................................................... 1

1Introduction .................................................................................................... 1

1.1Problem Definition .................................................................................... 1

1.2Scope And Objectives ............................................................................... 2

1.3Research Hypothesis ................................................................................ 3

1.4Methodology: ........................................................................................... 4

2Chapter 2 ......................................................................................................... 7

Theoretical Framework ..................................................................................... 7

2.1Introduction To The Concept Of Resistance ............................................... 7

2.2Introduction To The Concept Of Resilience .............................................. 8

2.3Shifting Concepts Of Landscape .............................................................. 10

2.4Resilience Of Landscapes ........................................................................ 11

2.5Comparative Analysis Of Resistance And Resilience As A System And

Response Paradigms 11

2.5.1Resistance And Resistance Management ....................................... 12

2.5.2Resilience And Resilience Governance .......................................... 13

2.6Vulnerability ........................................................................................... 16

2.7Summary: Resistance, Resilience And Vulnerability ................................ 17

Chapter 3 ......................................................................................................... 21

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3CLIMATE CHANGE....................................................................................... 21

3.1Global Climate Change And Sea Level Rise .............................................. 21

3.2Sea Level Rise And Nile Delta ................................................................. 22

3.3Implication Of Climate Change And Sea Level Rise On Nile Delta .......... 25

3.4Vulnerability Of Coastal Region:............................................................. 26

3.4.1Focus Zone: ................................................................................. 26

3.4.2Methodology Of Assessment: ........................................................ 27

3.5 . Estimation Of The Impact On Low Elevated Coastal Zones Of The Coastal

Region: ........................................................................................................ 28

3.5.1Estimation Of Impacted Distribution By Region (Governorate) In

LECZ Of Alexandria, El Beheira And Kafr El Shiekh: ............................ 30

3.5.2Estimation Of Impacted Population In LECZ Of Alexandria, El

Beheira And Kafr El Shiekh: ................................................................. 31

3.5.3Estimation Of Impact Built Up Areas Located In LECZ Of

Alexandria, El Beheira And Kafr El Shiekh: .......................................... 34

3.5.4Estimation Of Impact Agriculture Lands Areas Located In LECZ Of

Alexandria, El Beheira And Kafr El Shiekh Impact On: ........................ 35

3.5.5Distribution By National Income: ................................................. 38

3.6Conclusion And Reflection: .................................................................... 40

Chapter 4 ........................................................................................................ 43

4Hard Measures In Coping With SLR ............................................................. 43

4.1Current Coastal Protection ...................................................................... 43

4.2Sea Level Rise Design Responses ............................................................ 44

4.3Resistance: Hard Engineering Approaches ............................................. 47

4.3.1Groin ................................................................................. 48

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4.3.2Seawall And Dikes ........................................................................ 48

4.3.3Offshore Breakwater .................................................................... 50

4.3.4Artificial Headland ........................................................................ 51

4.3.5Examples Of New Technologies ..................................................... 51

4.3.6Maeslant Barrier Rotterdam ......................................................... 51

4.4Implication Of Hard Engineering: ........................................................... 53

4.5Alexandria: Case Study For Resistant Paradigm: ..................................... 54

4.5.1Historical Evolution And Present Circumstances: ......................... 55

4.5.2Alexandria Development Pathways .............................................. 57

4.5.3Shore Line Analysis: Measures For Coastal Protection For

Alexandria 58

4.6Implication Of Flooding Event On The Coastal Area Of Alexandria ........ 64

4.6.1Protected Areas: ........................................................................... 64

4.6.2Unprotected Areas: ...................................................................... 65

4.6.3Assessment Of The Adaptation Measure Implemented In The City

Of Alexandria ................................................................................. 68

4.7Implementation Of Hard Measures: ....................................................... 68

4.7.1Softening The Shoreline ................................................................ 69

Chapter 5 ......................................................................................................... 74

5PARADIGM SHIFT ....................................................................................... 74

5.1Introduction To Paradigm Shift ............................................................... 74

5.2Models For National And International Action ........................................ 76

5.3Flood Design Practices ............................................................................ 78

5.3.1Hafen City-Hamburg: ................................................................... 78

Chapter 6 ........................................................................................................ 82

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6CASE STUDY 2: NEW MOTOBUS ................................................................ 82

6.1Development Pathways Along The Nile Delta: ........................................ 82

6.2Coastal Planning Laws: .......................................................................... 83

6.3Case Study 2: New Motobus ................................................................... 84

6.3.1Location And Site Analysis: ........................................................... 84

6.4Current Proposed Master Plan: .............................................................. 86

6.5Methodology: ......................................................................................... 88

6.6Setting The Goals ................................................................................... 89

6.7Defining The Strategies: ......................................................................... 89

6.8Measures For Increase Community Resilience ........................................ 91

6.9Off Shore Measures: ............................................................................... 92

6.9.1Artificial Reefs: ............................................................................. 92

6.10Ecological Buffer Zone: ......................................................................... 92

6.10.1Wetlands .................................................................................... 93

6.10.2Shore Stabilization Structures ..................................................... 94

6.10.3Advantages Of Soft Measures:..................................................... 95

6.11Inland Development .............................................................................. 96

6.11.1Zoning And Setbacks ................................................................... 96

6.11.2Building Codes And Regulations: ................................................ 98

6.11.3Compact Design Development .................................................... 101

6.12Green Infrastructure And Roads: ........................................................ 102

6.12.1Open Spaces: ............................................................................. 102

6.12.2Storm Water Management: ....................................................... 103

6.12.3Roads: 103

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7Conclusion ................................................................................................... 105

References: ..................................................................................................... 111

List Of Figures: .............................................................................................. 120

List Of Meeting .............................................................................................. 125

Arabic Summary ............................................................................................ 128

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List of Figures

Figure 1 : Methodological Frame Work .............................................................. 5

Figure 2: Resilience and Resistance related terms ........................................... 10

Figure 3: Climate Change and the coastal system showing the major climate

change factors, including external marine and terrestrial influence. ................ 12

Figure 4: Conceptual Model of Resistance, Resilience and Vulnerability ......... 18

Figure 5: Global GHG emissions in the absence of climate policies ................. 22

Figure 6: The world vulnerable coastal deltas: ................................................ 23

Figure 7: Nile Delta ......................................................................................... 24

Figure 8: Impact of 0.5m SLR on the Nile Delta .............................................. 24

Figure 9: Impact of 1m SLR on the Nile Delta ................................................. 25

Figure 10: Geographical allocation of Alexandria, El Behiera and Kafr El Shiekh

....................................................................................................................... 27

Figure 11: Low Elevated Coastal Zones (Digital Elevation Model) of Alexandria,

El Behiera and Kafr El Shiekh ......................................................................... 29

Figure 12: Geographical Distribution of Population Density in Alexandria, El

Beheira and Kafr El Shiekh ............................................................................. 33

Figure 13: Geographical Distribution of Low Elevated Urban Areas Vulnerable

to 0.25, 0.5 and 1 m SLR in Alexandria, El Beheira and Kafr El Shiekh ........... 35

Figure 11 : Geographical Distribution of Low Elevated Agriculture lands

Vulnerable to 0.25, 0.5 and 1 m SLR in Alexandria, El Beheira and Kafr El

Shiekh ............................................................................................................. 37

Figure 15: Geographical distribution of GDP per Capita in Alexandria, El

Beheira and Kafr El Shiekh ............................................................................. 39

Figure 16: Current protection Status of the Coastal Region ............................. 44

Figure 17: Adaptation Strategies Response ...................................................... 46

Figure 18: Groin Design .................................................................................. 48

Figure 19: Undermining of a seawall built on a high energy coastline ............. 50

Figure 20: Maeslant Barrier ............................................................................ 52

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Figure 21: The Dutch Oosterschelde Storm Surge Barrier ................................ 53

Figure 22: Alexandria Historical Evolution ....................................................... 57

Figure 23: Alexandria shoreline ...................................................................... 60

Figure 24: Alexandria Shoreline cont. .............................................................. 61

Figure 25: shore line evolution from 1950-2010

Figure 26: Effects of 2010 storm wave on coast ............................................... 65

Figure 27: Unprotected community of Abu Qir (Urban Poor) .......................... 67

Figure 28: Break Water Tower ......................................................................... 71

Figure 92 : A step-type seawall incorporating a bench of both mangroves and

saltmarsh......................................................................................................... 72

Figure 30: Shots of the seawall at KogarahBay, Georges River, showing a step-

type seawall with a bench of salt marsh vegetation. ......................................... 72

Figure 31: Hafen City Master Plan ................................................................... 79

Figure 32: Residential units overhanging a waterfront .................................... 79

Figure 33 : Elevated Roads in Hafen City ........................................................ 80

Figure 34: Open Spaces in Hafen City ............................................................. 80

Figure 35: Proposed Strategic Land use Plan for the Nile Delta ...................... 83

Figure 36: Regional Analysis of New Motobus ................................................ 85

Figure 37: The evolution of the Rosetta Shoreline during the past two centuries

....................................................................................................................... 86

Figure 38: Current proposal for Motobus ...................................................... 88

Figure 39: Division of Coastal Area ................................................................. 92

Figure 40: Scenarios for different lot subdivision and setbacks for mitigation

and reduce impact associated with flooding .................................................... 97

Figure 41: Scenarios for different lot subdivision and setbacks for mitigation

and reduce impact associated with flooding cont. .......................................... 98

Figure 42: Shore line transect illustrate Zones Classification of recommended

Buildings ....................................................................................................... 101

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List of Tables

Table 1: Comparative Analysis between two paradigms of Resistance and

Resilience (Source Author) .............................................................................. 15

Table 2: The Population and area of Aleandria, Behiera and Kafr El Shiekh .... 27

Table 3: Low Elevated Coastal areas with high potential impact on Alexandria,

El Beheira and Kafr El Shiekh ......................................................................... 30

Table 4: Estimation of the Impacted Population to the SLR, in Alexandria,

Beheira and Kafr Elshiekh Governorate ........................................................... 31

Table 5: Estimation of the Impacted Urban Area to the SLR, in Alexandria,

Beheira and Kafr Elshiekh Governorate ...........................................................34

Table 6: Estimation of the Impacted Agriculture Lands to the SLR, in

Alexandria, Beheira and Kafr Elshiekh Governorate ........................................36

Table 7: Disadvantages of Hard Measures ....................................................... 53

Table 8: Lessons of nature applicable to Design and Construction (Source:

Watoson D. and Adams M. 2011) ..................................................................... 75

Table 9: FEMA Federal Emergency Management and Assistance (FEMA) Flood

Plain Management Strategies .......................................................................... 76

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Chapter 1

1 Introduction

1.1 Problem Definition

Climate change, the world upcoming threat, is predicted to have dramatic

effects on the coastal communities with associated impact of; sea level rise,

storms surges, flooding events, erosion and other natural hazard (IPCC 2007).

Sea Level Rise (SLR), will be one of the major consequence of CC on the coastal

regions, associated with stresses such as flooding risks, high erosion rate, salt

water intrusion and many other natural hazard. Along with other non climatic

stresses that interact with the CC which include, over exploitation of resources,

pollution, decrease in the availability of fresh water, sediment reduction and

urbanization (Nicholls and Branson, 1998). This will represent an additional

stresses to the socio-economic and environmental aspect with special regard on

systems that undergo continues and growing pressure accompanied. This

constitute one of the major challenges to the coastal development, which is the

integration of the physical, social and economic processes and the associated

uncertainty of its dynamic nature (Nicholls and Branson, 1998).

The Egyptian coast is highly vulnerable to the impact of sea level rise (OECD

2004) Such a rise in sea level will significantly impact coastal areas in Egypt.

The Nile delta is highly exposed to several climate-change related hazards and

risks. In the context of assessing the impact of sea level rise on the Egyptian

coast, there are major challenges that affect Egypt's northern coast when it

comes to current and upcoming climatic changes.

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1.2 Scope and objectives

The value of this study is to the aim to guide stakeholder in coastal communities

to develop more resilient strategies, plans, agendas, to confront the threat of

SLR. The main aim is to transform the current mind set of the effects of climate

change away from defense and opposition to that adapt and even prosper in

time of uncertainty; and to understand and explain the idea of resistance and

resilience and understand the consequences of each development paradigm by

investigating the capacities and vulnerabilities of each system and approach,

upon accepting that hard engineering solution are robust and outdated.

Main objective trying to understand the difference in approaching the issue of

SLR when it comes to complex existing cities (Alexandria) and new virgin cities

(motorbus) by tackling the two paradigms of resilience and resistance.

Table (1) presents the main aim and objectives of the study in hand.

Aim Objective Chapter

Investigate main

theories and

definition

To define the concept of coastal

landscape and boundaries of

coastal system

To understand resistance and

resilience and vulnerability

concepts and their interrelation

Chapter 2

Explore different

Coastal systems

vulnerability

To explore global climate

change's effect on sea level rise in

Egypt

Setting fact base and calculation

of Vulnerability

Chapter 3

Present Current

adaptation

measures

To understand coastal evolution

of area under investigation

Resistant Paradigm and hard

measures in Alexandria

Chapter 4

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Aim Objective Chapter

Understanding

global adaptation

models to SLR

Understanding the need in

Shifting Paradigm

Chapter 5

New Coastal

Development

Understanding threats that

confront new development of the

coast

Proposing guide lines and

understanding for new

development

Chapter 6

1.3 Research Hypothesis

Currently, methods of resistance (Hard Measures) are being implemented to

protect coastal landscape and environment, this result in continuous natural

degradation, misuse of the natural resource and causing robust and disengaged

relationship between human and the natural environment, seeking more of

establishing economical foundations rather than any environmental

consideration. Never the less encouraging overuse, and discouraging

conservation, which could be significant to adaptation to the impacts of climate

change.

This paper is to postulate that in dealing and planning new cities, resilience is a

paradigm in dealing with new urban developments. As it offer more holistic

approach in tackling and handling change.

The study will be based on the assumption that coastal development in new

coastal cities like Motobus will not be conducted as a continuation of the former

pathways, or existing practices, in the coastal development (as for instance in

Alexandria). This is not just based on a mere hypothetical assumption but

rather the projection of the trends and development pathways that are evident

now.

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This will start by exploring the Egyptian experience in dealing with flooding and

coastal dynamics, which is claimed hereby to be a resistant approach.

Therefore, it is important to study the biggest example of dealing with sea level

rise in Egypt Delta applying resistant strategies, and to search for an alternative

example to go from here to more suitable and future-oriented cases.

The aim is to provide comprehensive strategies for new coastal cities taking into

account the dynamics between nature and society, not just resisting change but

also possibly embracing it. This approach targets to set the foundations for a

new resilient strategy, characterized by flexibility, cost efficiency, achieved by

embedding the society into the natural context.

The coastal development is still undergoing in the highly vulnerable areas,

hence the need for a new paradigm to be proposed at New Motobus (extension

of the existing city) or newly developed coastal cities, unlike previous measures

that were used in complex cities.

1.4 Methodology:

The study will be based on collective research on different practices in dealing

with the coastal region and protection measures. Upon the completion of

defining the main objectives, the study will start by defining and

conceptualizing the main concepts of Resilience and Resistance and set the base

for understanding its relation with the coastal communities and setting the

main framework. Following, it will set a fact base and understanding of the Nile

Region (The Selected Zone). Then will continue by analysis of the current

practice along the region with a focus study on Alexandria as the biggest

example in dealing with coastal communities in Egypt. Hence, proposing new

strategies for coastal community of New Motobus. This will be accompanied by

presenting general case studies that propose practical approaches in dealing

with coastal communities.

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Figure 1 : Methodological Frame Work

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2 Chapter 2

Theoretical Framework

The following chapter is an attempt to Defining (Conceptualizing) the

characteristics and factors that develop Resistant and Resilient and the

interplay of the dynamic relation between them with regard to periods of

gradual change (the impact of sea level rise and not to withstand that these

relations change depending on the temporal, social, and spatial scale)

2.1 Introduction to the Concept of Resistance

In broad terms, resistance is defined as “the refusal to accept or comply with

something”. (Oxford Dictionaries). In ecological literature the concept of

resistance describes the intention of the system of avoiding and fending off

disturbance. In the first place, this implies the refusal to change, taking every

measure necessary to not let the threatening event happen (Kline 1998). The

general stance of a resistant attitude can be described as violent and determined

opposition. So resistance is directly related to preventing or protecting

measures, which means every effort is done to make it impossible for a

particular event to happen. This necessarily leads to a high level of protective

measures and, consequently, to high cost as argued by (Klein and Nicholls

1999)

Further, it is important to note that a resistant attitude or philosophy inherently

implies not considering the failure of the protective system as a realistic option,

since everything is done is done to prevent it happening. Hence, no provisions

usually are taken to react to, or cope with, the (as perceived) effects and

consequences of an unlikely, or even impossible, failure of the system under

strain. This drawback can be considered as one of the main weaknesses of

resistant philosophies.

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For this reason, adaptive change or accommodation to the effects of a hazard

are not envisaged, and hence no provisions taken for it, in a resistant system. In

a sense, there is only on definitive line of defense.

2.2 Introduction to the Concept of Resilience

The term resilience has become a prominent topic that recently emerged in

dealing with changes and confined within the discourse on climatic change. The

resilience concept was originally introduced by Holling, (1973) in the field of

ecology aims at understanding the dynamic development process of ecosystem

and the maintenance of their functions.

The resilience of a system is defined by two ways in the ecological literature,

with different character in achieving stability. The first was introduced by

Holling C. S in 1973, who defined it as the ability of a system to persist its

relationships in times of disturbances, and resist the displacement from its

original state. However, this, in a strict sense, also applies to most resistant

systems. The question thus appears to be crucial to which degree the resilient

system is willing and capacitated to diverge from its original state, before

returning to it eventually. Here lies another fundamental difference to resistant

systems. This measure is significantly smaller in the case of resistant systems.

In this context, resilience is considered as the time or speed in which the system

returns to a pre-existing condition after disturbance; it is defined as

“engineering resilience” (Holling, C. S. 1996). A clear distinction needs to be

done in understanding, the difference between the resistance and engineering

resilience. They both address the common domain of stability (pre-existing,

referenced state). However, resilience, with its explicitly temporal dimension, is

constituted characteristically by the time of return. Resistance, on the other

hand, offers more robustness but shows more inflexibility.

The other definition of resilience, defined as “ecological resilience”, of Ecology

(Holling, C. S. 1996) is the commonly used definition. The approach was then

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introduced within different disciplines and extended to various fields. Walker

et. al. (2004) defined resilience as follows: “Resilience is the capacity of a

system to absorb disturbance and reorganize while undergoing change so as

to still retain essentially the same function, structure, identity, and feedbacks.”

The approach was then introduced within different disciplines and extended in

various fields. Walker et. al. (9001) defined resilience as “the capacity of a

system to absorb disturbance and re-organize while undergoing change so as to

still retain essentially the same function, structure, identity and feedbacks”. The

appearance of the perspective of socio-ecological systems by Folke, C et. al.

(2002) draws an emphasis on the role of the actors involved and their role as an

integral part in the decision process of increasing the adaptability of the system.

Resilience, as a general concept, can be described both in a literal and a

figurative sense. The former is applied to a material or object which is capable

of returning or springing back into its initial shape after having undergone

significant deformations, for example under the action of force. The latter is

used for characterizing any organism or system which is able to recover quickly

from severe difficulties, also to be understood as a sign of toughness. The

crucial feature of this strategy or capacity, especially as opposed to the converse

concept of resistance, is the ability of the system under strain to adapt initially

to the external action, at the same time undergoing significant change. The

capacity to absorb change but to subsequently return to the initial state without

significant disturbance, hence, is one of the main features of resilient systems

and stands in stark contrast to the point-blank refusal of resistant systems to

admit changes.

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Figure 2: Resilience and Resistance related terms

2.3 Shifting Concepts of Landscape

The term landscape was frequently almost exclusively associated with beautiful

sceneries of meadows, forests, greenery, mountains, etc. However, the recent

definition of landscape acquires a meaning which goes far beyond "beautiful

landscapes"(Seggern H et, al 2012). The boundaries of the system are not easily

defined given the dynamics and frequent changes confronting the coast. Coastal

ecosystems are among the most productive, and yet highly vulnerable,

environmental systems in the world—as they are essential for services’

provision (UNEP 2011). At the same time, these systems are confronting rapid

environmental degradation as a consequence of frequent land mismanagement

and urbanization.

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2.4 Resilience of Landscapes

The concept of Resilience and the new perception of landscape both offer better

understanding in adapting and managing the dynamics of systems. According

to Prominki, M. (2010), the new landscape concepts consider planning and

designing landscapes as operations with evolutionary systems and recognize the

interaction of man and environment. The resilience concept can be considered a

nonlinear approach dealing with the dynamics and uncertainty of disturbances.

Hence, understanding landscapes with respect to resilience to climatic change is

a prominent topic in planning and designing coastal landscapes that is

confronting changes

2.5 Comparative Analysis of Resistance and

Resilience as a System and Response Paradigms

Nicholls, R.J., (2007) defined coastal systems as "the interacting low-lying areas

and shallow coastal waters, including their human components. This includes

adjoining coastal lowlands,” […]. “In addition to local drivers and interactions,

coasts are subject to external events that pose a hazard to human activities and

may compromise the natural functioning of coastal systems" (See fig. 3). [p.318]

The coast system is subjected in many terms to external events that impose

damages to human activities and threaten the natural balance of the coastal

system. Beaches, rocky shorelines and cliffed coasts differ from deltas, Estuaries

and lagoons, Mangroves, salt marshes and sea grasses, coral reefs. Severe

consequences for human society and activities on freshwater resources,

agriculture, forestry and fisheries, Human settlements, infrastructure and

migration, human health, biodiversity, recreation and tourism result (Nicholls,

R.J., 2007)

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Figure 3: Climate Change and the coastal system showing the major climate change factors,

including external marine and terrestrial influence.

It remains unclear though the dynamics of the development confronting the

coastal systems in dealing with climatic change. Resilience is not necessarily

desirable in systems were social and economical aspects play an important role

(e.g. complex-mega cities). Hence these systems can be highly resistant to

change and seeking more stability rather than adaptability. Systems could

be resistant, yet not resilient (Ahmed, A. K. 2006). Therefore an

understanding of the interrelation of these development paradigms needs to be

done with distinguishing between resistance management and resilience

governance.

The following section tries to conceptualize the main concept behind the

resistant and resilience paradigms.

2.5.1 Resistance and Resistance Management

In case of external threat like SLR, regardless of the magnitude of the impact,

whether high or low, the associated consequences will initiate a disruption,

metaphorically described as a domino effect, causing the disturbances as well in

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the attached complex sub-systems of economic, physical, natural, social and

institutional. This could be derived whether, because no former provisions were

taken to cope with the hazard, or relying on one defense line in which any

deformation will cause the penetration of risk into the unprepared adjacent

system. This leads to a high level of measures, to high cost, which is a drawback

of his attitude.

In terms of response to external threat, the paradigm towards Resistant

Management can be considered a rigid top-down approach, a sole purview

of the state through government, which domineers or patronize the community.

Resistant systems tend to be highly centralized. Achieving a very high level of

security (resistance) requires also a tight management, which in turn requires

centralized structures. Community is a man-made system, which to a certain

extent is alien to, and threatened by, the natural hazard, which subsequently

tends to threaten the integrity of the community

This can be considered a typical approach of resistant systems directed towards

the prevention of the system from transforming into a new configuration when

exposed to external threat (SLR). It could be assessed and measured by the

Flexibility and mobilization of assets that keeps the functioning of the

community that if lost or damaged, and could cause significant disruption,

which includes jeopardizing social capital (population density and social

vulnerability, cultural asset, etc), Physical built and critical infrastructure

(building densities, construction, )..

2.5.2 Resilience and Resilience Governance

On the other hand, in recent literature, scholars defined Resilience as

“….related to three different characteristics: (a) the magnitude of shock that

the system can absorb and remain within a given state; (b) the degree to

which the system is capable of self-organization, and (c) the degree to which

the system can build capacity for learning and adaptation.” (C., Folk, cited by

Ahmed, A. K. 2006).

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The main aspect is that it is presenting a yielding capacity of the system

allowing the hazard, but at the same time having the ability to return back to its

original state or transforming into a new state without massive disruption. A

resilient system that allows too severe damages is will not be able to deploy

its advantages because this will prevent the system from returning to its original

state. So it’s always also an issue to keep the negative effects of the hazards

within a tolerable limit. A crucial point is the capacity to return to the original

state without suffering significant damage.

The impact associated with the hazard, high or low impact, has a gradual effect

upon the system. Various defense lines cause multiple scales of feedback

between the subsystems that constitute the whole system and allow adaptation

through a learning process, between the individual and the whole community;

and between the community and the surrounding sphere of local and national

or even international scale. Community in this case acts as an integral part of

nature, which absorbs the shock of natural hazard. The resilience approach

emphasizes on the role of the actors and promotes their participation. Different

forms of complexity are to be taken into consideration with a high level of

sophistication in the interrelation between subsystems, combining strong

properties and flexibility. This enables the system to act as a whole in adapting

change.

In the governance theories, it is highly emphasized that response is not just a

top-down approach, but rather interaction between many actors involved,

including the community, private sector, developers, NGOs, etc. (Lebel, L. et al,

2006) The decentralization of institutions, and organizational diversity, support

the capacity of the system (government, community, organizations, etc) to

better handle of the complexity of the systems (Duit, A. et al. 2010).

Table 1, present the summary of the comparative analysis between the two

paradigms.

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Table 1: Comparative Analysis between two paradigms of Resistance and Resilience (Source

Author)

Resistance

Resilience

Definition The refusal to accept or

comply with change

Capacity of a system to absorb

the disturbance without losing

it main function

Approach Resistance Management

Resilience Governance

Centralized

Top down approach one way

Balance between centralized

and Decentralized

Multi-scale responses

Response Domino effect in case of

external hazard causing the

disruption of the attached

systems of economic, built

physical, natural social and

institutional

Cause multiple scale feedback

allowing learning process,

between individual,

community, local and national

scale and between the

community and the

surrounding environment

Complexity High level of complex robust

configuration, create

Complexity of the system

with its multi-layered flexible

responses, as compared to the

physical complexity of

resistant systems.

Community High dependence on

authorities

Community is integral part

of nature, which absorbs the

shock of natural hazard.

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2.6 Vulnerability

The high concentration of the economic activities and livelihoods on the coastal

region increase its vulnerability, with high level of impact. The threat that

confronts the coastal region could be highly similar in the magnitude.

Vulnerability as defined by the IPCC is "the degree to which a system is

susceptible to, or unable to cope with, adverse effects of climate change,

including climate variability and extremes. Vulnerability is a function of the

character, magnitude, and rate of climate variation to which a system is

exposed, its sensitivity, and its adaptive capacity"(2001 p.21)

According to the definition of vulnerability, it implies three different concepts in

dealing with perturbation and hazards, which are: exposure, sensitivity and

adaptive capacity.

The former, exposure, Refers to the level of external threat. Some areas are

more exposed than others just because of their geographical location for

instance. This applies to lowlands, which are more susceptible to be flooded. So,

in a sense, exposure is a consequence of external factors related to the context.

On the other hand, sensitivity: This refers to the configuration of the system

itself. Depending on how it reacts to external hazards. A complex system might

be sensitive, a more robust and simple one less sensitive.

Adaptive Capacity – A combination of all the strengths and resources available

within a community, society or organization that can reduce the level of risk,

or the effects of a disaster. (Capacity may include physical, institutional, social

or economic means as well as skilled personal or collective attributes such as

leadership and management. Capacity may also be described as capability.)

(UN/ISDR, 2004 cited by Levina E. and Tirpak D. 2006 [p.9])

Vulnerability is a state prior to response; it does not just depend on the type of

response but also on the external factors that define the threat or hazard.

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However, some regions can be considered more vulnerable than others

according to various aspects, including the assets available in each zone.

Mueller, B. (2011) showed that there is a lack of common understanding of the

factors that make regions resilient and other vulnerable due to the complex

character that constitute the regional social, economic, cultural and political

systems

2.7 Summary: Resistance, Resilience and

Vulnerability

The concept of risk occurrence contains probability; there are two opposing

paradigms of Dealing with Sea Level Rise: The response paradigms might be

resistant or resilient. Increasing the protection of the coast questionably

increased the resistance of the overall system on account of the resilience (Klein

and Nicholls 1999). There is a necessity to achieve a balanced relation between

the protection of the community-with its economic and social aspects- and the

degradation of the natural environment of the coast.

Resilience and resistance of system is always affected by human influences, but

not necessarily having a negative impact. Planned adaptation can serve to

reduce the vulnerability through enhancing resilience and resistance.

Vulnerability is determined not only by exposure susceptibility of the potential

impact; it will also inherent in the resilience of the system which include the

society’s technical, institutional, economical and cultural capability to prevent

or to cope with change (Turner et al 2003).

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Figure 4: Conceptual Model of Resistance, Resilience and Vulnerability

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Chapter 3

3 CLIMATE CHANGE

The main aim of this chapter is offer better understanding of the coastal region

and explore the potential impact of SLR on Nile Delta that act as a fact base.

The analysis will be selected three governorates Kafr El Sheikh, El Beheira,

Alexandria.

3.1 Global Climate Change and Sea Level Rise

The climate change is inevitable, the upcoming global threat confronting

especially the coastal communities. Global SLR is the most recorded and

obvious consequences of climate change. It is an issue that threats and

contributes to multitude of high risks especially to highly populated coastal

communities, infrastructure and natural resources. The major challenges of CC

include, rising temperatures, changing precipitation rate, and increasing

frequencies of extreme weather conditions, the rise of the global mean sea level,

frequent flooding, shoreline erosion, and many other natural hazards. Sea level

Rise is a result of different natural phenomena and more resulted from

anthropogenic reasons. The continuous increase in green house gas emissions

resulted in the SLR due to the ocean’s thermal expansion, glacial melt from

Greenland and Antarctica, which are the most dominating factors affecting SLR

(Dasgupta, et al., 2007). The melting of the Greenland and Antarctic ice sheets

holds amounts of water that can increase sea level rise almost by 70m

(Elsharkawy H., 2009). Global scenarios present high uncertainties regarding

the variation of SLR. Estimate of SLR in this century by the IPCC projections

(Fourth Assessment report 2007) are between 0.18 and 0.59 m by the end of

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the century (sea fig. 4). However, more recent global scenarios also indicated,

suggesting higher global SLR by the year 2100, ranging between 80 and 200 cm

(Pfeffer et al.2008) and 50–140 cm (Rahmstorf 2007)

Figure 5: Global GHG emissions in the absence of climate policies

3.2 Sea Level Rise and Nile Delta

SLR is one of the major challenges that confront the Egyptian North Coast. The

Nile Delta is among the most vulnerable coastal Deltas to the impact of SLR

with settled population above one million local inhabitants.

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Figure 6: The world vulnerable coastal deltas:

Presenting the Nile Delta potential population to be displaced by 2050 (Extreme = >1 million;

High = 1 million to 50,000; Medium = 50,000 to 5,000)

The Nile delta is extended from Alexandria in the west to Port Said in the east;

cover about 240 km of the Mediterranean Sea coast line. It is one of the main

resource supplies for Egypt. It is rich with it diverse coastal systems,

agriculture, aquaculture, and is highly vulnerable to inundation and salt water

intrusion from the projected SLR (OECD 2004). Nile Delta is highly vulnerable

to several climate-change threats with almost 30% of Nile delta vulnerable to

SLR. Gharib, S. et al., (2013) evidence from 6 beach locations in Egypt has been

assessed during the period from 1939 to 1980, which showed that, during those

fifty years, the sea level increased by an amount of about 11.35 centimeters. This

area Rosetta and Damietta on the Mediterranean coast, as the studies have

confirmed, experienced a significant decline in the shore line in the modern era

in comparison to what it was in the nineteenth century (Source Frihy. O, Khafay

1991). (See fig. 6, 7 and 8)

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Figure 7: Nile Delta

Figure 8: Impact of 0.5m SLR on the Nile Delta

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Figure 9: Impact of 1m SLR on the Nile Delta

3.3 Implication of Climate Change and Sea Level

Rise on Nile Delta

High population is settled in low-lying coastal regions, the majority of

population will be affected the impact of SLR. SLR will be associated with other

events which are as following:

1. Coastal Erosion due to the extreme weather conditions that drive

storm-surges towards coastal cities that increase the erosion rate which

is a result of currents to beaches with gradual shift and deposition of

sand in another area. The rates of this phenomenon have already

increased after the construction of the High Dam due to the loss of

ecological balance, which led to large quantities of silt being deposited

on the beach (Gharib S., et al 2013).

2. Land subsidence, which can be perceived as a virtual rise in sea level due

to tectonic changes in the earth's crust of the region is another evident

phenomenon. It is also influenced by the high rate of pumping

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groundwater or oil Gharib, et al 2013). The measurements conducted

during the last five decades revealed that the sea level rose about 2 mm /

year in Alexandria and 4 mm / year in Port Said (El Raey 1999).

3.4 Vulnerability of Coastal Region:

Climate change will increase the risk for coastal population and urban

settlements, especially for the highly concentrated population in low elevated

areas, or directly exposed with no protection (Feiden, P. 2011). This will pose

stresses on the coastal region and will contribute with high shares in rendering

the human communities and coastal landscapes into a different configuration

(Mcgranahan, G., Balk, D. and Anderson, B. 2007).

The migration from the coastal areas could require huge external forces and

efforts, and would be associated with high cost and would be very difficult to

implement without massive disturbance. It is liable to develop into a central

questions for individuals, policy makers, and will centre on the issue of how will

be a high degree of resilience (adaptation) of the coastal communities

(landscapes) attained.

The following section seeks to understand different socio-economical and

natural parameters that contribute to the vulnerability of the coastal regions

and to understand what makes coastal regions to be considered more

vulnerable than others, even with relatively equal share in the potential threat.

3.4.1 Focus zone:

The analysis of the following study will be conducted in the coastal area of three

governorates, Alexandria, Behiera and Kafr El Shiekh (see fig. 9). The available

data will be considered in the assessment and used in analyzing the distribution

of the population, function, uses and properties of the coastal regions. This will

be conducted through assessing the size and magnitude of the impact of SLR on

human livelihoods and the distribution of population along the coast (selected

Zone), trying to give an overview of scale and magnitude of the potential SLR.

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Table2, presents the total area of the governorate and population according to

the area gathered from Geo database and CAPMAS (2006)

Table 2: The Population and area of Aleandria, Behiera and Kafr El Shiekh

Area sq.km Population (mil)

Alexandria 2.93004E+15 4.3

El Beheira 6.36896E+15 3.97

Kafr El Shiekh 2.94305E+15 2.6

Figure 10: Geographical allocation of Alexandria, El Behiera and Kafr El Shiekh

3.4.2 Methodology of assessment:

The following analysis it adapted from integrating recent spatial geo-database

(GIS) - adopted from the GOPP on the Nile Delta- The assessment is based

upon the different coastal layers provided, of topography, buildup, water

aquaculture, vacant-undeveloped land, governorate and administrative limits.

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The added data set of the 2006 population (CAPMAS) and GDP1 per capita.

Based on the available data, the analysis has been developed by overlaying of

data input. Overlaying of the available data with consideration of the 0.25, 0.5

and 1 meters SLR scenarios, the precision of the data can be considerably

influenced by the overlay of the geographic data set and its accuracy.

3.5 Estimation of the Impact on Low Elevated

Coastal Zones of the Coastal region:

On a regional perspective, high percentage of land area, population and

economic activities are present in areas located below mean sea level in the Nile

Delta.

Figure 10 present the topography of the three governorates Alexandria, Beheira

and Kafr El Shiekh; showing that high percentage of the governorates areas are

located in Low Elevated Coastal Zone (LECZ) and highly exposed to the impact

of SLR.

1 GDP per Capita according to the (Human development report 2003) were the highest district republic wise is Ma'adi of 19274 GDP per Capita and 1753.4 is in Dar EL Salam

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Figure 11: Low Elevated Coastal Zones (Digital Elevation Model) of Alexandria, El Behiera and

Kafr El Shiekh

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3.5.1 Estimation of impacted Distribution by Region

(Governorate) in LECZ of Alexandria, El Beheira and

Kafr El Shiekh:

Vast areas of land in the governorates will face high impact associated with the

threat of SLR as high percentage of the land allocated in low coastal zone areas.

El Behiera has an estimate of 14% (904.9 sq. km) of its total area to be lost in

case of 0.25 SLR, following Kafr El Shiekh and Alexandria of 8.7% (259.5

sq.km) and 9.5% (356.8 sq.km) of total governorate areas (See table 3). This

includes high fertile agriculture lands, urban settlements, water bodies

(including fish farms, lakes, wetlands, salt marches) and other vacant or

undeveloped lands.

Table 3: Low Elevated Coastal areas with high potential impact on Alexandria, El Beheira and

Kafr El Shiekh

Alexandria El Behiera Kafr El Shiekh

Current Area

Sq. km 2930.03 6368.95 3736.13

0.25m SLR

Sq. km 256.57 904.99 356.89

% 8.7% 14.2% 9.5%

Num. of

districts 11 7 9

0.5m SLR

Sq. km 276.33 1010.66 601.17

% 9.4% 15.8% 16.0%

Num. of

districts 12 7 11

1m SLR

Sq. km 301.25 1731.60 2060.71

% 10.2% 27.1% 55.1%

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Num. of

districts 12 8 12

3.5.2 Estimation of impacted population in LECZ of

Alexandria, El Beheira and Kafr El Shiekh:

Coastal populations are at high risk from SLR. It becomes evident from the

variation of the district areas and the distribution of the population along the

coastal zone. Figure 12, presents the geographical distribution of population

density based on the statistical calculation of the population on the district area,

mainly to show the higher concentration of population along the region. Kafr El

Shiekh and El Beheira have considerable lower population density concentrated

in the coastal region in comparison to Alexandria. The population of low

elevated areas, in the selected focus zone, amounts to about 1.8 million

inhabitants of the total of the focus zone population. They are highly vulnerable

to the threat of seawater intrusion, which is due to the fact that about 16% of the

total population is located in prone areas. Based on the estimation of the

impacted Population exposed to the SLR, in Alexandria, Beheira and Kafr

ElShiekh in absolute numbers, the potential population located in LECZ, is

estimated to be 1.25 million inhabitants for 0.25m SLR and 1.5, 1.92 million

inhabitants for 0.5 and 1 meter SLR, making 29, 35, 44% of the total percentage

of the governorate with no consideration of the high growth rate the city is

witnessing. (See table 4). Following, El Behiera governorate, in which 0.47,

0.53, 1.15 million inhabitant living in LECZ will be highly vulnerable for 0.25,

0.5 and 1m SLR consequentially; making 12, 13 and 29% of total population of

the governorate. Finally Karf El-Shiekh, 0.0982, 0.14 and 0.20 million

inhabitants are vulnerable for 0.25, 0.5 and 1m SLR.

Table 4: Estimation of the Impacted Population to the SLR, in Alexandria, Beheira and Kafr

Elshiekh Governorate

0.25m SLR 0.5m SLR 1m SLR

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Populati

on

(Mil)

% of

Governo

rate

Populati

on

% of

Governo

rate

Populati

on

% of

Governo

rate

Alex. 1.25 29.09 1.518 35.31 1.92 44.73

Beheira 0.47 12.07 0.534 13.46 1.151 29.00

Kafr 0.098 3.77 0.145 5.60 0.204 7.88

Total 1.82

2.198

3.280

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Figure 12: Geographical Distribution of Population Density in Alexandria, El Beheira and Kafr El

Shiekh

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3.5.3 Estimation of Impact built up areas located in LECZ

of Alexandria, El Beheira and Kafr El Shiekh:

It is highly evident that there is a considerable variation in the distribution of

urbanization, so as the distribution of population in LECZ, (Fig.13). The highest

shares of population densities are concentrated and living in districts with high

urbanization rate, which is the coastal zone of Alexandria.

A total area of 40.66 sq. km is allocated in low elevated coastal zone of the focus

zone. An area of 21.79 sq. km is located in low elevated coastal zone area of

Alexandria, and will be impacted by 0.25 m SLR making 21.78sq. km 24.6 % of

total urban settlement, whether urban cities or rural communities. Followed by

El Beheira with 15.31 sq. km counting 24% of total urban area, finally Kafr El

Shiekh with the least percentage of low elevated coastal urban areas making

3.57 sq. km.

Table 5: Estimation of the Impacted Urban Area to the SLR, in Alexandria, Beheira and Kafr

Elshiekh Governorate

0.25m SLR 0.5m SLR 1m SLR

Area sq.

km

% of

Urban

Area

Area sq.

km

% of

Urban

Area

Area sq.

km

% of

Urban

Area

Alex. 21.78 24.67 26.38 29.884 33.33 37.75

Beheira 15.31 11.88 16.89 13.10 35.15 27.28

Kafr 3.57 3.97 5.63 6.26 25.85 28.77

Total 40.66

48.9

94.33

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Figure 13: Geographical Distribution of Low Elevated Urban Areas Vulnerable to 0.25, 0.5 and 1

m SLR in Alexandria, El Beheira and Kafr El Shiekh

3.5.4 Estimation of Impact Agriculture lands areas

located in LECZ of Alexandria, El Beheira and Kafr

El Shiekh Impact on:

The agricultural sector is one of the main productive sectors of the Nile Delta. It

will be highly impacted considering that vast areas are allocated in the low

elevated coastal zone (see figure 14).

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El Beheira acquires the highest share in the agriculture areas, being considered

one of the main land use activities. An area of 813 sq.km (13.42%) will be highly

exposed in case of 0.25 SLR; and increase in case of 1m SLR to 25.4% of the

total area. Followed by Kafr El Shiekh making in absolute figures area of 257.89

sq. km, in case of 0.25 m SLR and reaching area of 1375.2 sq km making 46.7%

of the agriculture lands. Alexandria comes last in the agriculture area lost,

making up an area of 99.6 sq.km of 12.7% of agriculture land, with slight

relative increase in case of 1m SLR an area of 103.76 sq. km. (see table 6)

Table 6: Estimation of the Impacted Agriculture Lands to the SLR, in Alexandria, Beheira and

Kafr Elshiekh Governorate

0.25m SLR 0.5m SLR 1m SLR

Area sq.

km

% of

Agricultu

re Land

Area sq.

km

% of

Agricultu

re Land

Area sq.

km

% of

Agricultu

re Land

Alex. 99.6 12.78% 102.3 13.13% 103.76 13.30%

Beheira 813 13.42% 890.9 14% 1539.17 25.40%

Kafr 257.89 6.90% 404.27 13.70% 1375.2 46.70%

Total 1170.49

1397.47

3018.13

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Figure 11 : Geographical Distribution of Low Elevated Agriculture lands Vulnerable to 0.25, 0.5

and 1 m SLR in Alexandria, El Beheira and Kafr El Shiekh

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3.5.5 Distribution by National Income:

The vulnerability of coastal areas against coastal hazards depends partially on

its contribution to the GDP per capita. It is not necessarily that coastal regions

with high population have higher contribution to the GDP. However, it is highly

noticeable from the high shares of Alexandria’s population to the GDP. This is

associated to its regional and economic importance. Figure 15 presents the

geographical distribution of GDP per Capita in Alexandria, El Beheira and Kafr

El Shiekh. District with high contribution to the GDP are mostly located in

Alexandria, otherwise the share is similar in its contribution to the GDP.

Coastal districts with lower contribution to the GDP do not underscore the

lower vulnerability, however high contribution of a district to the GDP leads to

taking more part in the political negotiation in confronting the threat of SLR.

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Figure 15: Geographical distribution of GDP per Capita in Alexandria, El Beheira and Kafr El

Shiekh

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3.6 Conclusion and reflection:

Climate change is an inevitable phenomenon that has major consequences on

the coastal regions. The Nile delta is one of the most vulnerable Deltas in the

world, as high area percentage is located in low lying areas that makes SLR will

have high contribution to natural and human environment recourses losses.

This will urge global, governmental, nongovernmental, individuals at different

scales to contribute to mitigate the risk associated with the hazard.

Upon the completion of the geographical distribution of the statistical analysis

on the coastal region and understanding the potential threat confronting the

area, the planning approach need to direct preliminary adaptation efforts that

increase ability of the urban community to cope with change, a new approach to

better understanding of the risks and the impact associated with the hazard

with consideration of Incremental change.

On the regional perspective, it gives a geographical presentation and relation

between the coastal districts, in terms of regional importance, economic and

population concentration that contribute higher to the political negotiations in

SLR risk reduction.

Alexandria in comparison to the other coastal governorates (El Beheira and

Karf El Shiekh) has the highest shares of attention, not only because of its

regional and political importance, but also high concentration of socio-

economic activities. It is considered the biggest example in the country that

deals with coastal problems in will be analyzed in a later section of this

document.

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Chapter 4

4 Hard Measures in Coping with SLR

This chapter will try to explore the general measures that are commonly used to

prevent flooding into the coastal communities and investigate its impact on the

coastal communities. Then will present Alexandria as an example for the

biggest example for coastal protection.

4.1 Current Coastal protection

As was presented in the previous section, the coastal zone in Egypt is highly

vulnerable to the issue of the SLR in particular, given the high concentration of

the socio-economic activities as well as high population rate (Ericson, J.P 2006)

According to the OECD report (2004) all measures that outlined for the coastal

protection in Egypt are considered as a response for the current development

pathways along the coast and synergistic to the SLR. Nevertheless, it is not

covering all vulnerable areas of the coastal region. All the measures used are

restricted towards “hard measures”. These measures for coastal protection that

have been implemented to improve the stabilization of the coast for example:

extension of break waters in Alexandria (World Bank 2010) beach

nourishments projects, reinforcement of the Abou Qir sea wall –that was

constructed 1780- (OECD 2004).

The figure 16, shows areas of hard measure protection, natural protection and

unprotected areas, along with the most sensitive areas along the region.

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Figure 16: Current protection Status of the Coastal Region

4.2 Sea Level Rise Design Responses

IPCC Response Strategies Working Group (1990) identified three main

adaptations strategies to cope with SLR which are as following:

Retreat: "Retreat involves no effort to protect the land from the sea.

The coastal zone is abandoned and ecosystem shifts landward this

choice can be motivated by excessive economic or environmental

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impact of protection. In the extreme case, an entire area may be

abandoned."

Accommodation: "Implies that people continue to use the land at

risk but do not attempt to prevent the land from being flooded. This

option include erecting emergency flood shelters, elevating buildings

on piles, converting agriculture to fish farming, or forming flood –or-

salt- tolerance crops.

Shoreline protection:"involves hard structures such as sea walls

and dikes, as well as soft solutions such as dunes and vegetation, to

protect the land from the sea so that existing land uses can continue. (p.

135,136) see figure 16.

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Figure 17: Adaptation Strategies Response

According to the IPCC fourth assessment report (2007), coastal regions will

eventually confront an increase in the sea level that might have irreversible

impacts. Thus, there is an urge to provide measures to prevent and enhance the

coastal regions. Conventional planning paradigm according to Godschalk, D.

(2003) considers hazard mitigation:

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Towards protecting the people, assets and environment form the

potential hazard or threat.

Directing new development projects away from the vulnerable areas and

relocating the existing land use towards new safer areas and limiting

development in flood prone areas

Seeking hard and structural measures in confronting the threat such as

flood control work, shore hardening as an attempt to reduce the impact

associated with the hazard

According to Watson, D. and Adams, M. (2011) there are two types of measures

for shore protection which is known by:

Hard, structural and Engineered and;

Soft, non structural or Natural

4.3 Resistance: Hard Engineering Approaches

The resistance approach tends to prevent water intrusion into the system and

allowing robustness on flexibility. Hard structural/engineering measures are all

implemented by artificially constructed structures on the beach or offshore. Its

robust nature allows no flexibility and it builds up a boundary between the

natural and human environment and prevents the continuation 0f natural flow.

These are resisting measures to any integration between the shore and the

adjacent community, its main function being to block the sea water intrusion

into the land. It is constructed to halt the coastal processes and disruption so as

to reduce their implication of the adjacent community (Braatz, S., et al, 2007).

Hard measures include dikes, levees, seawalls, revetments, bulkheads, groins,

detached breakwaters, floodgates, and saltwater intrusion barriers. These are all

constructed for flood prevention (IPCC 1990).

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4.3.1 Groin

Groin is constructed perpendicular to the coastline, to prevent sediment

transport and control the shore erosion (U.S. Army Corps of Engineers. 2002;

Braatz, S., et al, 2007). The main design aim is towards maintain a minimum

width of the beach and to control the sand movement along the shore.

Braatz, S., et al, (2007) elaborated that a variety of materials could be involved

in the construction of the groins which involve rocks, woods etc.

Disadvantages:

Require continuous maintenance

Require more than one structure to function

Figure 18: Groin Design

4.3.2 Seawall and dikes

The primary purpose of seawalls and dikes is to prevent flooding into the

adjacent land from extreme wave conditions due to tidal fluctuation. The main

functional design is to increase the elevation of the structure to prevent the

overflow of water into the land.

A seawall is built from a concrete structure parallel to the coast line and dikes

are built from earth structures that keep elevated water from flooding. (U.S.

Army Corps of Engineers. 2002; Braatz, S., et al, 2007).

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The disadvantages of a seawall:

It generates wave reflections and support sediment transport offshore.

It does not sustain beach steadiness.

High possibility of erosion occurrence on the shoreline if not

constructed along the whole coast line (Braatz, S., et al, 2007)

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Figure 19: Undermining of a seawall built on a high energy coastline (source: CCD 1997 cited by

Huettche, C.M., et al. 2002)

4.3.3 Offshore breakwater

Breakwaters are constructed parallel to the coastal shoreline. Its main function

is to absorb the wave energy. There are types that are submerged underwater,

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which might become multi-functional artificial reefs where aquatic habitat can

develop, and thus enhance their existence. They are huge structures and

relatively difficult to build. (U.S. Army Corps of Engineers. 2002; Braatz, S., et

al, 2007).

Disadvantage:

It requires special design

The structure is exposed to Extreme wave action. (Braatz, S., et al, 2007)

4.3.4 Artificial Headland

Artificial headland is used to create a steady beach behind it (Braatz, S., et al,

2007). It is constructed from a rock structure similar to other combined

measures directed to promoting natural beaches through providing sufficient

sand for a stable beach profile and restoration of eroded beach.

The disadvantages are:

It is a relatively huge structure.

It reflects waves and cause downdrift of the protected coastline.

Week stability confronting large waves.

4.3.5 Examples of New technologies

There are new combined technologies which were developed and constructed to

protect the coastal communities from flooding. The following are two major

examples that were established in the recent years.

4.3.6 Maeslant Barrier Rotterdam

The Maeslant Barrier is a high-tech modern barrier. It is an example of

the Dutch civil engineering practices. It is built to protect Rotterdam

and its surroundings from flooding events. Maeslant Storm Barrier is

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designed having two huge movable arms. It closes the waterway in an

automatic manner whenever storm occurs. Closing the barrier is done

fully automatically, even the notification of the ships, eight hours before

closure, is done without any human intervention. (Rotterdam city guide

n.d.)

Figure 20: Maeslant Barrier

4.3.6.1 The Dutch Oosterschelde Storm Surge

Barrier

One of the biggest construction works for protection in the Netherland from

against frequent flooding from the North Sea developed after a devastating

storm surge in (1953). It is one of the largest coastal engineering work to

combat the extreme storm surge and protect the lands from flooding. It was

constructed between Schouwen-Duiveland and Noord-Beveland islands.

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Constructed from series of dams and storm surge barriers. Doors are normally

open, but close under extreme weather conditions. (The Official Cite of Holland

n.d.)

Figure 21: The Dutch Oosterschelde Storm Surge Barrier

4.4 Implication of Hard Engineering:

There are many examples around the world where mankind is attempting to

control his environment. The implementation of hard engineering measures

into coastal communities contributes highly to natural and ecological damage

(Grannis, J. 2011). Hard engineering does not solve the coastal problems, but

often causes problems elsewhere, providing only a temporary fix. The following

are the main disadvantages of implementing the hard measures. It acquires

environmental, economic and social dimensions:

Table 7: Disadvantages of Hard Measures

Sector

Disadvantages

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Economic

Hard engineering defense can be more costly

It provides only a temporary solution and requires

regular maintenance and replacement

If the measure is breached, the water is trapped

and it is difficult to drain it back to the sea

Environmental

Hard engineering creates many environmental

impacts. It disturbs the sediment movement.

It redirects the wave energy increasing the erosion

on neighboring land and increases soil-salination

on the land.

It prevents upland migration of wetlands and

contributes to the erosion of beaches.

Social Protects the land only to a certain limit.

It is not aesthetically satisfying

It has a high tendency to increase urbanization

adjacent to the hard structure, therefore increases

the vulnerable population in the flooding events.

It constitutes a hard armoring obstacle access to

the coast and prevents the public using its

recreational value.

4.5 Alexandria: Case Study for Resistant Paradigm:

Alexandria is can be considered the biggest example in Egypt biggest example in

Egypt in Dealing with coastal hazards. It is presented as an example that follows

the follow Resistant paradigm in dealing with coastal hazards.

Alexandria is the most important city along the coastal region and considered

the biggest example in Egypt for urban communities dealing with coastal

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planning. The city is stretches about 60 km along the coast, from Abu Qir in the west

till Sidi Kirir in the west. It has population of about 4.5 million (CAPMAS) inhabitants

with one million increases in summer which makes it one of the main destinations

for all Egyptians. The city hosts 40% of about the total Egyptian industries as

well as the largest harbor in the country. (El Raey et al 1999).

It has founded historical, economical and social foundation from the former

centuries. Alexandria’s harbor is the main harbor in Egypt. It is the center of

high trade and marine commerce.

4.5.1 Historical Evolution and Present Circumstances:

The city was originally established with the vision of linking Alexandria

with "Pharos" island. By wharf from rocks was established connecting the

city with the island and this was considered to be the backbone of the

later development and to the moment is considered the core urban

structure in the city. It created a natural division of the port into the

Eastern and Western ports. The area is currently known as "El Mansheya

and El Gomrok". (Alex. Governorate (1984),) the city has passed through

several historical eras, Romans and poltamic, Christianity, French

colonial.

The modern Alexandria is a foundation to the infrastructure and

planning of Mohamed Ali. The importance of the economic and

military value of Alexandria was significant until it became the second

capital of Egypt (Alex. Governorate 1984). The infrastructure that was

set in the Mohamed Ali era is considered the foundation of the further

development that followed till the recent years. There were different

factors affected this:

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1. The digging of El Mahmoudeya Canal in year 1819 leading to

reclamation of lands along with the recovery of the activities in the

port.

2. Introduction of cotton cultivation in Egypt and using

Mahmoudeya Canal to transport it to Alexandria and then export

it.

3. Increase the depth of the port and creation of new platform which

had the biggest impact in the return of Alexandria to its old glory

times

4. Construction of new railway "Cairo-Alexandria" by year 1854

made Alexandria directly connected to Suez and increased the

transit commerce in Alexandria

5. Providing the city with public services which increased the

immigration towards it

6. Establishment of passengers railway by year 1876 that affected the

urbanization, building, storages and companies

(Alex. Governorate (1984)

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Figure 22: Alexandria Historical Evolution (source: Alex. Governorate, 1984)

4.5.2 Alexandria Development Pathways

Alexandria’s development pathways in the recent years have increased even

with the city’s high exposure to the impacts of climate change, erosion, flood

inundation and storm surges and not to withstand the over-capacity of the

existing infra-structure. Field surveying and development indicators show

that the city is currently expanding into low elevated (lying) rural hinterland

near Lake Maryout and Abou Qir depression and experiencing rapid

population and economic development (Personal communication with

Essam Fouad, 2013). Alexandria’s coast line and hinterland are highly

vulnerable to inundation and submersion as a consequence of sea level rise

and coastal erosion and considered according to Nicholls, R. J. et al. (2008)

on the top the top-ten cities in terms of exposed population and around 30

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US$ bil exposed assets. A detailed study was done by El Raey (1997) which

showed that Alexandria’s almost 1.5 million inhabitant are vulnerable to the

threat of SLR, if no action is taken, with 195 443 risking total loss of

employment Evidence of extreme whether condition occurring in Alexandria in

the past few years was recorded. See Table8

World Bank Report ES1 presented that the most challenging aspects in the

present and future development:

1. One third of the city are informal areas

2. Low elevated areas

3. Ill maintained infrastructure will be a huge challenge in the future to

cope with the change

4. Areas confronting the Coastline with high proximity to the sea

4.5.3 Shore line Analysis: Measures for Coastal Protection

for Alexandria

Higher authorities of the city pay out US$300 million for coastal protection

measures for the shore line protection (Batisha A. F. 2012). However, according

to El-Sharnouby, B. and Soliman, A. (2010) there is neither integrated

coastal management nor a strategic plan developed for the shoreline

protection. Each zone has been protected in a different measure and with a

different type of structure. Groins, revetment concrete blocks, sea walls, are

all considered to be hard methods of confronting the coastal dynamics.

These protection measures have been implemented along the beaches of

Alexandria in order to overcome the erosion and to prevent the waves’

energy from attacking the shore. The evolution of the shore line presented in

figure (23 and 24) clearly describe the transformation process on the shore

line during the area of 1950 to 2010 with the addition of lagoon harbor

jetties groins as well. The following section will elaborate the coastal protection

measure that is being used by the city.

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Figure 23: Alexandria shoreline

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Figure 24: Alexandria Shoreline cont.

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Figure 25: shore line evolution from 1950-2010

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4.5.3.1 Groins and Beach nourishment:

Depositing sand in the eroded beaches (El Raey, M. 1999) by sand transferred

from the western desert (Personal communication with Karim Rakha, 2013)),

which acts as a buffer area between shoreline and urban agglomeration also it

acts as a touristic sand beach (EL Raey 1999). Groins, as well are constructed

perpendicular to the shore in order to use them with nourishment groins, as it

provides a space for recreational beaches. According to El Raey, M. (1999) and

field survey presented that usage of groins has a high public acceptance and

very fair environmental performance in comparison to other measures.

4.5.3.2 Breakwaters:

Breakwaters are constructed along the shoreline from natural stones and

rubbles to decrease the storm impact. Recent work has been done from Miami

Beach to Montaza. It consists of rubble, sand stones, or concrete blocks. It

includes elevated and submerged parts. There are off-shore submerged

breakwaters which act as a breaker of the wave/storm energy. (World Bank

Report)

4.5.3.3 Sea Walls and revetment blocks:

The revetment concrete block is the most dominant shore protection measure

along the coast. Storm surges are the most dangerous meteorological

phenomena along the coast and have a strong impact on it.

Dekhiela and Mohamed Ali wall are two main sea walls that have been formerly

constructed. Mohamed Ali Sea wall was constructed in the 1780 to prevent the

penetration of water into the low elevated areas located behind it (1.5-2.5meter

below sea level rise). For that matter, it is considered to be one of the main

sensitive structures along the coast responsible for the protection of agricultural

lands and hinterland. It was recently maintained (1989) by addition of

additional concrete blocks and a sloping face. However, there is sub-surface

leakage area (F. Essam 2013)

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4.6 Implication of flooding event on the Coastal Area

of Alexandria

Different aspects are included in the vulnerability of the exposed group of the

coastal community in Alexandria. Whether geographic distribution (low

elevated areas, hinterland, rural, urban, etc) or income generating socio

economical related characteristics (wealth, income, sector, etc) protected or

unprotected districts. The following will focus on the implicated of storm events

on the coastal environment of Alexandria

4.6.1 Protected Areas:

Evidence of extreme weather conditions occurring in Alexandria in the past few

years was recorded. According to B. El-Sharnouby and A. Soliman (2011);

Alexandria witnessed extreme weather the city was confronted for two days

with a wind blow of 65 kilometer per hour that created a wave with a height of

7.5 meter. This has resulted in severe damages along the shore line. This had a

negative impact on the shore protection structures and created a severe damage

to the coast (see fig 26).

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Figure 26: Effects of 2010 storm wave on coast (Source: El-Sharnouby B. and Soliman A., 2010)

4.6.2 Unprotected areas:

In terms of social equity and contribution to the shares of shore protection

measures along the coast, direct informal areas are evident along the coast

(Author Field Survey).

The community act as the first defense line with no measures of protection

towards coastal hazard, Abou Qir district make a good example of low income

social development and extension along the Alexandrian coast. Abou Qir

located South El-Montazah, El-Raml, Moharam-Bey and El-Amriya districts are

a community in Montazah District, with population of 200,000 inhabitants

(CAPMAS 2006). It represents one of the most important historical places in

Alexandria, with ongoing underwater excavation for lost monuments. It’s

considered as an eastern gate to Alexandria.

The highly exposed groups coastal (urban) poor that are located in the northern

eastern of the city, living directly along the sea with no protection measures.

Highly endangered as they are closely to the main sea wall of Abou Qir, which is

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considered the weakest point preventing water intrusion in to the adjacent low

land.

The main characteristics of this community are:

1. Illegal high buildings on the waterfront of Abu Qir (Alexandria

governorate, 1997)

2. Presence of slums in scattered areas, deteriorated buildings with

bad conditions and very narrow streets which cannot supply

many areas with efficient infrastructure (waste, water supply,

electricity) which lead to many environmental problems.

3. Post revolution Illegal construction in many areas including the

sea shore leading to the presence of unplanned streets and

narrow corridors

4. Waste water problems resulted from lack of drainage pipe supply

leading to draining into wells or directly into the sea.

5. Clear degradation in the aquatic environment and water

pollution which is no obstacle for the community to use sea

features.

6. Transportation problem is one of the major issues accessibility is

through one main road and main train line connecting it with

Alexandria main station.

The community in cases of any coastal hazard is the first defense line without

protection measures. Based on field survey findings, the 2010 extreme storm

surge had reached the building's third storey causing sever damaged to the

physical built environment. On the other hand the locals are adapting the

winter climate events and the damages cost with no willingness to resettle.

Figure 23 show the direct exposure of Abu Qir District to the sea and present

the environmental degradation situation. (See figure 27)

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Figure 27: Unprotected community of Abu Qir (Urban Poor)

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4.6.3 Assessment of the adaptation measure implemented

in the city of Alexandria

El Raey (1999) in his study assessed several adaptation measures, which include

beach nourishment, groins, legal development regulation, ICZM, and land use

change. The results showed that the best adaptation options in terms of cost

effectiveness is towards beach nourishment and breakwater in terms of net

benefit, environmental impact, robustness/flexibility, chances of success,

feasibility and fairness. However, it will be very difficult to implement a land

use change strategy or legal development regulation. The former is a result of a

high level of complexity that it will require for implementation, whereas the

latter will face the difficulty to enforce regularization putting into consideration

the local socioeconomic behavior.

4.7 Implementation of Hard Measures:

According to Watson, D. and Adams, M. (2011) and Pope (1994) mentioned that

hard measures only give a false sense of security as there might be a storm that

overcomes the structure and breach into the community. However, there are

some circumstances and situations where hard engineering measures can be

considered the only appropriate solution despite its various implications:

Highly dense urban environment

Places with critical infrastructure and architecture or intensely

urbanized areas which are at high risk

Large cities might find it quite challenging to accommodate spaces for soft

measures and hence, directed to more long term hard measures and strategic

approach to ensure its protection. (Grannis J. 2011). However, their impact on

natural environment cannot be avoided. However there are measures can be

taken to reduce the impact and harshness of the hard measures.

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Different measures can be added to mitigate the harshness and robustness of

hard coastal protection; yet their effect on the natural environment is

inevitable.

4.7.1 Softening the Shoreline

There is a necessity to achieve a balanced relation between the protection of the

community-with its economic and social aspects- and the degradation of the

natural environment of the coast.

The following will present some visionary projects that aim to soften the hard

measures implemented in the coastal region and increase the ecological

dimension along with the protection measures.

4.7.1.1 New York City Proposal:

The project “On the Water” offer proposals for the waterfront development of

the city of New York/New Jersey with adaptation dimension to confront the

threat of CC and associated impact of SLR, flooding and storm surges.

The plans focus on the revitalization and increase of the ecological responses to

restore the waterfront of the city. The proposed adaptive measures are flexible,

aiming to replace the current hard measures applied, and to reduce and to

mitigate the impact. Measures like wetlands, piers, park, oyster beds and

artificial islands are all newly proposed measures for the waterfront.

(Nordenson G., et al., 2009)

ELEVATED HIGHWAY WITH NEW LANDSCAPE

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WIDE LANDSCAPE

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BREAK WATER TOWER:

1. Floating boardwalk for recreational

access

2. Suspended vegetation provides shelter

for birds

3. Inorganic material absorb water as

tide barriers

4. Mussel farms

5. Cold water kelp forest provides shelter

for fish

6. Oyster beds

Nordenson G., et al., 2009 [p. 198]

Figure 28: Break Water Tower

4.7.1.2 Environmental Friendly Sea Walls:

Sydney Metropolitan Catchment Management Authority and Department of

Environment and Climate Change NSW (2009) presented proposals for

softening sea walls which include providing artificial reef habitat immediately

in front of seawalls, providing variation of texture and form on the seawall

surface, Maximizing habitat diversity and complexity, Maximizing the use of

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native riparian and estuarine vegetation, the increasing the artificial reefs by

introducing Reef Balls to increase habitat.

Figure 92 : A step-type seawall incorporating a bench of both mangroves and saltmarsh.

Figure 30: Shot of the seawall at KogarahBay, Georges River, showing a step-type seawall with a bench of salt marsh vegetation.

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Chapter 5

5 PARADIGM SHIFT

5.1 Introduction to paradigm shift

Climate change should not be perceived as a threat for coastal development, but

rather an opportunity to provoke new ways of for planning cities. The effects of

SLR are not just limited to the coast. The protection measures mentioned before

help cities to prevent the damages or reduce the impact on the build

environment. It gives false sense of security as there is always a chance of a

storm surge that is above the protection level of the engineered structure

(Watoson D. and Adams M. 2011).

This implies an understanding that natural environment and shift from the

conventional paradigm, from controlling the natural environment thinking, to

be directed to learn from nature dynamics and learn to live with change. Table 9

present Lessons of nature applicable to Design and Construction adapted from

Watoson D. and Adams M. (2011). Design for resilience is a prominent

paradigm in dealing with planning and designing new cities to confront the

threat of SLR (Watoson D. and Adams M. 2011; Gunderson D. 2003). The need

to create a shift from resistant- top down-hard – conventional planning

paradigm to creating environmental friendly, thriving, amphibious, flexible and

resilient cities. This will require integrating the climate change in the initial

planning process and develop more a holistic, integrated approach that

understands and integrates the dynamics of nature with the surrounding

communities and avoid a robust community and to be directed towards more

flexible and adaptive responses that are adjusted to the changing conditions.

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Resilient communities are considered an antidote to reduce or eliminate coastal

vulnerability (Bently, T 2009). Resilient cities are constructed to be strong and

flexible, rather than brittle and fragile (Gunderson D. 2003). Their physical,

build systems of infrastructure, utilities, and other facilities are planned

to meet code standards based on hazard mitigation in order to still

function in the face of climate fluctuation. (NOAA 2009).

Resilience aims to design new cities strong and adaptable rather than fragile

and weak and to continue functioning in front of the climatic events, rather

than break and collapse. Also make best use of nature rather than relocation

into safer areas (Gunderson D. 2003).

The lifeline build up systems of buildings, infrastructure, roads and utilities are

constructed to meet the certain criteria according to the hazard threat. Elevated

buildings, planning with consideration of erosion and inundation, setting up

zoning, setbacks, and infrastructure are all measures that contribute to

adaptable community to SLR (Gunderson D. 2011;NOAA 2009).

Table 8: Lessons of nature applicable to Design and Construction (Source: Watoson D. and

Adams M. 2011)

Lessons of nature applicable to Design and

Construction

Absorption: Watershed planning

and design (reservoirs, retention

ponds, green roofs)

Buffering: Break, riparian

buffer, rain garden, shuttering.

Core Protection: Zoning,

Decentralization, self –reliant

subsystems.

Diffusion: Meanders, wetland

Rapid responses: Smart grid, early

warning, emergency responsive

systems.

Redundant circuits: Green

Infrastructure, wildlife corridors, and

multiple service routes.

Storage Capacity: aquifers,

wetlands, reservoirs, cisterns.

Waste/ Nutrient recovery:

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and coastal zone landscape, often

foundation.

sustainable storm water design and

waste systems.

5.2 Models for National and International Action

The Federal Emergency Management and Assistance (FEMA) Flood Plain

Management Strategies (2009) compiled different lessons to mitigate the

impact of flooding on coastal communities. It defined four main strategies for

flood mitigation measures and which are: quoting:

Table 9: FEMA Federal Emergency Management and Assistance (FEMA) Flood Plain

Management Strategies

Strategy Tool

“Strategy 1:

Modify human

susceptibility to

flood damage”

Reduce

disruption by

avoiding

hazardous,

uneconomic or

unwise use of

floodplains. [p.I-

30]

It emphasize on using regulation of the land use

for flood plains and the usage of zoning tool to

draw development far from prone areas or

preserving natural areas, introducing codes for

developing subdivision, building and health and

sanitary codes.

Allocate land in the floodplain that work to

safeguard open spaces and permanently

relocate buildings.

Elevated or flood proof buildings and adjust the

present ones.

Increase community awareness of the hazard

occurrence through forecasting of the climatic

condition and flooding. Also provide early

warning and emergency plans.

Re-vitalization and protection of the natural

resources and maintain purposes of floodplains.

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Strategy 2:

Modify the

impact of

flooding

Assist

individuals and

communities to

prepare for,

respond to and

recover from a

flood. p.I-31]

Providing knowledge to increase the capacity to

of community to self-reliant in terms of

protection against flooding.

Adding emergency response throughout the

flooding event to protect the citizens and assets.

Minimizing the impact of flooding on the

financial sector by flood insurance and tax

regulation.

Arrange and propose post-flood plans and

programs to aid citizens to re-establish and

execute recovery procedures to protect from

further future events.

Strategy 3:

Modify flooding

itself

Develop projects

that control

floodwater p.I-

31]

Constructing dams and reservoirs to store

surplus water from urbanized areas.

Constructing dikes, levees and floodwalls to

prevent water from intruding into urbanized

zones.

Altering waterway canals to increase their

efficiency, so that over flow flooding will be less

frequent.

Redirect flows round urbanized zones.

Decrease the sealed surfaces and decrease the

run offs by increasing land permeability to

catch rain water to infiltrate the soil.

Gather excess runoffs and store them by on-site

detention measures.

Prevent the inundation on urbanized area by

using shoreline protection measures that

comply with the natural dynamic of the

shoreline.

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Strategy 4:

Preserve and

restore natural

resources

Renew the

vitality and

purpose of

floodplains by

reestablishing

and maintaining

floodplain

environments in

their natural

state

[p.I-32]

Regulating land use and direct urbanization

away from highly exposed or natural

environment. Might be a possible measure such

as floodplain, wetlands and coastal barriers.

Preserving the natural environment and ecology

through increasing open space, control land

acquisition, revival of natural habitat.

Include the community in the process of

preserving the natural environment by

increasing awareness toward the floodplains

and natural features.

Introduction of Taxes and flood insurance to

create initiatives for preserving and protecting

the natural environment.

Increase of soft measures in the protection of

the built environment.

5.3 Flood Design Practices

The following part will present models of cities that are seeking to achieve a

balanced relation between flooding events and built environment.

5.3.1 Hafen city-Hamburg:

Hamburg, Germany is currently developing the Hafen City to expand the city

center and creates a hub for trade and commerce. Hafen City is considered one

of the biggest examples of recent urban transformation for developing a city on

a contaminated site and tackling future-adaptive urban development. It is

located in a very attractive water front in Hamburg. (Neuauflage 2006)

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The city is located outside the main dyke system of Hamburg City in a very high

tidal area. The city is planned to cope with the natural tidal fluctuation and

flooding events.

Figure 31: Hafen City Master Plan

Buildings:

The buildings are all designed

elevated by 7.5 meter above sea

level to comply with the

regulation of the flood protection

system.

In addition, the basement is

designed to be sealed during the

flooding events.

Figure 32: Residential units overhanging a waterfront

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Roads:

Road system is designed away

from the water side so as not to

be affected by the flooding events

and with no access to the

buildings.

In addition, elevated routes are

designed to serve self refuge in

case of extreme flooding

condition. These are designed as

bridges and alike structures.

Open spaces:

The open spaces are designed to

cope with three levels of the tidal

dynamics. The spaces are used to

establish floating platforms

adapting to the tidal fluctuation.

(Prominski, M et al, 2012)

Figure 33 : Elevated Roads in Hafen City

Figure 34: Open Spaces in Hafen City

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Chapter 6

6 CASE STUDY 2: NEW MOTOBUS

6.1 Development pathways along the Nile delta:

Based on the study Presented by General Organization for Physical Planning for

Nile Delta Coastal Development (2010), Ministry of Housing and GOPP are

planning for new coastal development along the North Coast of the Delta.

Dividing the Nile delta into five main development sectors, for each sector there

are proposal for a new coastal communities and industries. The government

current approach is to direct the development of the coastal region toward the

urban expansion of the delta city toward the delta coast. New cities are being

proposed in the vulnerable areas of the coastal zone as an urban and economic

expansion of the existing cities. Cities like, West Gamasa, New Mansoura (9400

feddan)2, New Motobus (500 feddans),New Damietta (New Urban

Communities Authorities) (See figure32), and many other coastal cities. Huge

investment are being proposed to offer around 215 thousand new employment

opportunities in various fields for the main five development sectors, 175

thousand opportunities for industrial, touristic and services sectors, 40

thousand direct employment for agricultural land reclamation agriculture, With

total investment coast 4.3 bil EGP on total land 28368 Feddan.

2 Feddan is a measurement unit used in Egypt , which is equivalent to 2400 square meters,

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Figure 35: Proposed Strategic Land use Plan for the Nile Delta

Black color Represent new proposed urban communities

6.2 Coastal Planning laws:

No clear regulation for the coastal planning and development considering

impact associated with the climate changes and SLR in specific. Except for the

200 meter the beach premise zone, heavy construction is prohibited. The

environment law 4 issued 1994 is legal regulation that requires Environmental

Impact Assessment (EIA) prior to the implementation of any coastal project to

identify the impact on the coastal ecosystem (EEAA). However, there is no

proper enforcement of the law, there are projects have been encouraged to do

the assessment, however many others did not conduct the assessment (OECD

2004)

El Raey, M. (1999) and Hassan, M., et al (2010) and presented that in order to

reduce the economic losses due to inundation, future development must take

into account the potential threat of the inundation and SLR into account in the

initial planning process.

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6.3 Case Study 2: New Motobus

New Motobus is a new proposed city in Motobus district-Kafr El Shiekh

Governorate. The region has been long famous with its biological diversity,

remarkable landscape. The Governorate is planning for expansion and regional

growth. The vulnerability assessment that was conducted earlier, showed that

the selected region is located in very prone area along the coastal region and

highly exposed to the impact climate change and SLR.

The new proposed city is not yet established; however there is a preliminary

design proposal for the coastal community developed by (IDG. 2010). The main

aim of this section is to set the guideline principles for planning a resilient

coastal community.

6.3.1 Location and site analysis:

Motobus is located in Karf El Shiekh Governorate with the northern side is the

Mediterranean Sea, The southern border Fuh district, The western side is the

Nile River Rosetta branch and is considered the natural boundary between Kafr

El Sheikh governorate and El Beheira Governorate. On the eastern side borders

Sidi Salem Centre and Lake Burullus. It is highly connected to the regional

sphere as it is located directly on the International Road crossing the Egyptian

Coast to connect the North Arab Countries together.

Hassaan, M. A. and Abdrabo, M. A. (2013) pointed to the fact that natural and

manmade structure provide some protection to some areas. Such as the

international Coastal Highway which was constructed above sea level by 2

meters.

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Figure 36: Regional Analysis of New Motobus

Environmental threats confronting New Motobus:

The area is located in one of the most vulnerable and sensitive areas in the delta

coast. Along with other environmental problems the area is confronting which

are as following:

The potential sea water intrusion on the long term development.

Increase in storm surges

High erosion rate

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Frihy. O, Khafay (1991) monitored the evolution of the Rosetta Shoreline during

the past two centuries (between 1900 –1988) by positioning different historical

shorelines. The study showed shoreline retreat estimated by 53-58 (m yr-1t)

which is as a result of sediment inefficiency presenting high rate of erosion

along the Rosetta branch. Recent protection measures were added (groins) in

order to protect the shore line from further erosion.

Spatial data maps and measurement

of low elevated areas adopted from

GOPP GIS data base was used to the

proposed coastal zone change

projections for a proposed coastal

area. The Topography of the site it is

located in a low elevated coastal area;

with elevation between 0-1 meters

above sea level. (GOPP Digital

Elevation Model)

6.4 Current Proposed Master Plan:

The current proposed development master plan for the community in New

Motobus is proposed by IDG. (2010). Design planning measure where no clear

environmental studies are developed to cope with climate change. The coastal

building and planning measure for any coastal development is just to avoid

building heavy structures in the 200 meter the beach premise.

Figure 37: The evolution of the Rosetta Shoreline during the past two centuries

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The main aim to the proposed urban composition is focusing on the functions

and their relation towards each other and towards the coast.

Urban composition of the city:

- The simplicity and strong composition of the overall community

- The small outer perimeter of the city

- Forming open towards the Mediterranean coast

- Urban appropriate modulation of natural determinants

- The division of the city to functional areas

Land Use:

- The functional relationship between uses

- Balanced distribution of uses (residential and service sectors and

tourism)

- Linking domestic uses of Urban Mass With external uses.

- Clarity and ease of distribution uses

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Figure 38: Current proposal for Motobus

6.5 Methodology:

The design for New Motobus aims to introducing phase plans to cope with the

scenarios of SLR and tidal fluctuation in summer and winter. The main aim of

this section is to provide alternatives to mitigate and transform the convent

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communities Economic, aesthetic, diversity and political dimension are all

responsible factors for the growth development of coastal regions. The losses

accompanying coastal hazard events of ecological, socio-political, increases as

the development increases with increasing needs to replace local inhabitants

and compromise the natural ecosystem with population and development.

6.6 Setting the Goals

The area is highly vulnerable to flooding because of location in flood-prone

shoreline areas; aim to increase the adaptive capacity to cope with SLR. Any

adaptation strategies require formulation of set of goals in which are aimed to

achieve in order to increase the capacity of community to cope with uncertainty

and change NOAA (2010).

Reduce the vulnerability of the built environment to sea level rise

Maintain functioning and healthy coastal ecosystems

Introduce infrastructure capable to embrace the climate change impact

Minimize physical and economical losses associated with the impacts of

climate change

Protection of natural resources and capital

Increase awareness of community to flooding events and change

Improve the coordination between related institutions and

organizations

6.7 Defining the Strategies:

Strategy 1:

Stabilization of the shoreline to confront the SLR and coastal

erosion

Strategy 2:

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Setting sufficient buffer zone along the coast that is capable to

confront any external influences and considering the erosion factor

and allocate areas that absorb and diffuse storms and inundations

Strategy 3:

Increase the capacity of the floodplain landscape infrastructure to

absorb the flooding.

Strategy 4:

Enhance the ecological function, services and productivity

Strategy 5:

Create an environment that allow the community to interact with

nature and to be receiving and reacting to any external event

(flooding)

Strategy 5:

Create an environment that allow the community to interact with

nature and to be receiving and reacting to any external event

(flooding)

Strategy 6:

Protect the natural resources and capital by proper growth

management and development. Improve resilience of the

communities to climate change and variability through developing

legal regulation for zones and building and reduce the impact of

construction and develop construction codes to all systems of

buildings, infrastructure roads, utilities, and all measure that

contribute to adaptable community to SLR

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Strategy 7:

Increase adaptive capacity to manage climate change related risks to

fresh water availability by appropriate wastewater treatment

technologies and decrease use of potable water.

Strategy 8:

Improved public health, safety and social well being through

providing updated information about the threat and also provide

early warning to increase the awareness.

6.8 Measures for increase community resilience

The following climate change adaptation measures table is proposed for New

Motobus and could be highly applicable to new coastal communities. These

measures that are proposed to reduce the impact of the CC on the coastal

community. It is limited to measures that planners and architects have high

contribution and role for it. This measure might have multiple benefits and fit

into different categories. However they are categorized into their main function

and purpose according to the three main coastal zones:

1. Off shore: Water barrier

2. Buffer zone

3. Inland Development

It is a compilation from various sources aiming to guide growth and

development and offer measures to improve the adaptive capacity of the

communities to climate change effective planning in the initial phase reduce the

risk associated with hazard.

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Figure 39: Division of Coastal Area

6.9 Off shore Measures:

Off shore measure are mainly conducted to reduce the impact of storm surges

and inundation in to the adjacent community. The measures included mainly to

act as water barrier:

6.9.1 Artificial reefs:

Artificial reefs are constructed off shore, by placing man made material

underwater to revitalize or create and enhance an ecosystem especially to fish

habitat. It benefits the fisheries management, fishermen and increase economy.

It also functions as break water that diffuses wave energy and protects the

shoreline from erosion.(NOAA 2010)

6.10 Ecological Buffer Zone:

This is considered the main buffer area that acts as an intermediate zone

between the inland development/community and sea water. They are designed

to protect mainly the natural environment and ecosystem. They also have other

benefits and functions and could be a resource provider. They can provide

habitat, Catch flood water, diffuse its impact and decrease the intensity of water

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intrusion into the adjacent inland development, stabilization of the shore and

minimize the erosion rate.

It is design to protect the natural and built environment. It can provide

protective services and ecological dimension, providing habitat and natural

protection from erosion and flooding by stabilizing the soil, reducing the

inundation velocity and filtration of sediments (NOAA 2009). This can include

measures like:

6.10.1 Wetlands

Wetlands are one of the most productive ecosystems. It is a complex biological

system that an area of land that is partially, seasonally or permanently

inundated by water. It can be salt water or fresh water. NOAA Habitat

Conservation (no date) It combines several benefits:

- It creates a habitat for flora and fauna

- It act as natural bio-filter to remove the sediments and pollutants

- Act as an open space and acquire aesthetical benefits

It also has other benefits to flooding events:

- Control water inundation by regulating natural water flow and

accumulate water

However, constructed wetland can create a challenge in introducing it in the

coastal region as it require several research for its feasibility including the

nature of soil, topography, type of habitat etc. and high consultation to expertise

as it is highly engineered.

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6.10.2 Shore Stabilization structures

Stabilization of the shoreline to confront the SLR and coastal erosion, Setting

sufficient buffer zone along the coast that is capable to confront any external

influences and considering the erosion factor.

6.10.2.1 Beach nourishment:

Beach nourishment is used to increase the beach premise affected by sediment

loss or coastal erosion, by artificially increasing the amount of sand. This is to

maintain recreational value of the coast and replicate the mode the natural

beaches disperse wave energy. (U.S. Army Corps of Engineers. 2002;

Braatz, S., et al, 2007) This method requires continuous repairs and refilling

from the sediment source. It is used sometime to increase the efficiency of

some hard structure such as headland, groins and breakwaters. (U.S. Army

Corps of Engineers. 2002; Braatz, S., et al, 2007)

6.10.2.2 Dune enhancement/building:

Sand dunes are naturally formed along the coast, as they are development from

wind movement. An amount of sand gathered located within the landward

limits of tidal fluctuation. It offer ideal defense system as the coastal vegetation

is essential for the continued existence of dunes as the roots attach sediments

together and act as catchment and build up of sediment through the

windblown. The storm might affect the dune and grab the sand towards the sea.

However, in normal condition the wind blow back the sand to the dunes. (U.S.

Army Corps of Engineers. 2002; Braatz, S., et al, 2007)

6.10.2.3 Coastal Re-vegetation

The existence of vegetation in the coast increases the shore stability, strengthen

the sediment and decrease wave energy. It also protects the shoreline from

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erosion. However, some time it might be successful and others might not be

successful. Low energy environment have higher tendency to be successful than

in high energy environment. Failure may be due to:

The growth of some spices might not be adequate to site specification

and require certain environmental condition that might lead to failure

of the growth.

It is probable that human influences change the natural processes in the

area.

Clear indicator towards the suitability of introducing vegetation is the

already occurrence of vegetation already growing.

Other factors for example: slope, elevation, tidal range, salinity,

substrate and hydrology

(U.S. Army Corps of Engineers. 2002; Braatz, S., et al, 2007)

6.10.3 Advantages of Soft measures:

Soft-engineering provide tools which are flexible and adaptable, not

relying only on fixed measures.

Soft solution that copes with the nature dynamics provides the chances

to increase the ecological growth and increase living habitat.

Water purified by using natural measures. (Ex. Oyster beds, wetlands

and coastal vegetation)

Planting, vegetation and many other natural measures, increase oxygen

production and decrease carbon dioxide level. This contributes as well to

mitigate urban heat island effects. Moreover, they replace impermeable

and carbon intensive materials such as concrete and asphalt.

Soft measures, has low cost, require less maintenance and increase

saving by reducing demand on expensive infrastructure.

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6.11 Inland Development

6.11.1 Zoning and setbacks

6.11.1.1 Zoning:

In Coastal design zoning can be used to allocate and regulate the land use,

functions (multi-function spaces or infra-structure) building structure, shore

protection, setbacks, foot print) (NOAA 2009).Implementation of Zoning and

Overlay Zones in a SLR Context can divide the coast into two main zone

(Grannis, J. 2011):

V-Zones: are the front flood plains that are highly subjected to storm

velocity wave action. Hence, require more strict measures than other areas.

A-Zones: are inland/ upland areas of floodplains that will be highly

impacted to the 100 years flooding, but not directly subjected to wave velocity.

There are other categories outside the 100 years flooding zone with minimum

impact from coastal hazard. Each zone will require setting different

construction, mitigation measure. Figure presents the scenarios from direct

exposure with no construction consideration.

6.11.1.2 Setbacks:

Purpose of setbacks is to develop a buffer area to keep structures away from the

direct exposure and keeping distance from first lot require to be deep to keep

sufficient distance to protect the structure (NOAA 2010). Already before

purchasing a lot, information's about possible flood risk need to be sought for

from the municipality or from the competent offices of the Hydraulic

Administration. Defined based on a fixed shore line or vegetation line or to

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consider long term changes (like shore erosion rate). (Watson D and Adams

2011)

Figure 33, present different alternative for mitigating the impact associated

with flood through better subdivision of lots and including setbacks

Figure 40: Scenarios for different lot subdivision and setbacks for mitigation and reduce impact associated with flooding (source: Watson D and Adams 2011)

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Figure 41: Scenarios for different lot subdivision and setbacks for mitigation and reduce impact associated with flooding cont.)

6.11.2 Building codes and regulations:

Flooding can lead to significant damages of buildings and mechanical

equipment. The main reasons are, on the one hand, not considering the risks of

flooding when arranging the building lots, on the other, neglecting protection

standards.

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The level of the protection of the building depends of provision of building

codes enforced by the government or state. These codes could be applied to

address specific hazards. Sustainable building designs by developing legal

regulation for zones and building and construction codes, Building code

regulate design construction, Building code regulate design construction,

landscaping and aim to increase the capacity of the building to confront and

stand the external. (NOAA 2009)

Different building codes don't differ from different climatic zones and doesn’t

comply with the climatic situation in Egypt (Personal communication with

EEAA 2013).These codes could be applied to address specific hazards. A flood-

protected design means it provides sufficient protection of the construction

against flood to the extent that it is located below the level of the flood drain

zone. According to Petermandl, M. and Penninger, D. (2009), Austrian Building

Code From (1994) this, new buildings, annexes and renovations of buildings

within the zone of 30 and 100-year flood drain need to be designed and

constructed flood-protected.

Constructional Protection Measures

A flood-protected design means it provides sufficient protection of the

construction against flood to the extent that it is located below the level of the

flood drain zone

Raising Buildings

Within hazardous regions, raised construction type is often advisable.

For this purpose, soil can be heaped up or the building can be

constructed upon pillars. Also a slight rising of the door threshold can

avoid water penetrating during the flood.

Protecting Foundations against Erosion

Whenever a building is located within the floor area of flowing water,

there is at risk of the foundations being washed-out or even displaced. In

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order to avoid this, they should be executed deep enough, or otherwise

anchored or insured by means of an erosion protection.

Sealable basement

The sealing of the basement level is to prevent the building from being

inundated from flooding. Or basement can be sealed off with mobile

flood protection gates

Enclosure of the Lot / Outdoor Measures

Usually a building can be safeguarded by an encircling construction

protecting against high flood. For this purpose, stationary, partially

mobile flood protection walls can be used. Stationary measures are dams

or walls. Partially mobile measures are bulkhead or stop log systems in

combination with immovable fixing constructions.

Sealing Against Penetration of Water

Selecting appropriate materials is a fundamental measure for limiting

the damage is created by high flood. Water-resistant, preferably non-

porous materials should be used.

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Figure 42: Shore line transect illustrate Zones Classification of recommended Buildings

6.11.3 Compact design development

Compact design offer efficient grouping building and minimize footprint by

mixing of use and offering more open spaces that could be used as a ecological

infrastructure or wetlands migration corridors while protecting natural system.

Compact design means reduce the runoffs and reduce investment in the

infrastructure that is highly susceptible to hazard. It also increase the open

spaces which means reduce the run offs and flooding. Compact community

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design is better to be implemented with zoning and building restriction and

regulation in the development of the prone areas. (NOAA 2009; Jacob, J. and

Showalter, S. 2007)

6.12 Green Infrastructure and Roads:

Green infrastructure is a comprehensive approach that carries different

measures all together. It combine natural element of landscape into the

facilities of the community. This includes rain water management, open spaces

preservation, and tree landscaping as well sidewalk, utilities, and services

(Watson D and Adams 2011). Green Infrastructure could direct towards multi-

functionality as it related to water resource management and protection. Thus,

the usage of the soil and plants to store, divert, and treat water. (NOAA2010)

In order, for coastal communities to adapt to the inundation and the impact of

SLR. The need to increase the capacity of the drainage system, catchment

basins, flow direction and storage system through landscape infrastructure, this

includes:

6.12.1 Open spaces:

High urbanization rate increase the sealed surfaces causing in time of flooding

infrastructure might not be adequate to cope with change. replacing

impermeable surfaces by developing Multi-functional space aiming to protect

and provide habitat, mitigate the impact of flooding and runoffs, promote

ground water recharge, recreational aspect and enhance natural and cultural

resource. This has a contribution to increase and improve public space and

green areas and increase its quality, density, diversity of trees and landscaping

elements. (NOAA2010)

- Encourage ecological connectivity and habitat

- Reduce flooding and runoffs

- Promote ground water recharge

- Recreational aspect

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- Enhance natural and cultural resource

- Multi-functional space

- Create absorbent landscape, salt tolerant, adaptive vegetation to salinity

and water efficient

6.12.2 Storm water management:

The need for storm water management is to manage and contain the rain water

and generated runoffs. It can be used to reduce the risks to fresh water

availability by appropriate wastewater treatment technologies and Increase

capacity of storm water management systems to accommodate increased flood

waters it also plays an important role in protecting the built environment. Ill

equipped drainage systems to handle the storm water runoff may not be

adequate to handle future rainfalls events.

6.12.3 Roads:

The roads and accessibility play an important role in the security dimension for

the citizens’ safety and exit routes. The roads should be designed to safe refuge

citizens in case of extreme flooding events elevated above the level of the flood.

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7 Conclusion

Climate change is an inevitable phenomenon that is expected to have a

disruptive impact on the coastal region of the Nile Delta

In this study has explored two approaches in dealing with coastal planning:

“Resistant and Resilient paradigms”. The choice between Resilience/Resistance

mainly presets the system response to confronting the possible external event

and describes how the natural system will be affected.

Upon the completion of an initial general vulnerability assessment in the

coastal district in Egypt. It was clear that there is a significant variation in the

population and economic concentration along the low-elevated coastal region.

The higher the population of the community, the higher the risk will be that a

small impact could cause high magnitude of disturbance. Same applies for the

economic aspect: the higher its economic contribution of the district, the more

it draws higher priorities towards political interference.

However, there is still lack of consensus and common understanding of the

factors that make some regions resilient and others vulnerable (Mueler, B

2012). The resilience of the system or city or region with high economic activity

and governance system can rebound more quickly than that of another region

with less importance.

This is obviously clear, that the complexity of coastal cities causes them to be

highly resistant and robust to changing or adapting to the SLR. Cities like

Alexandria count the highest share in the level of complexity of planning for

resettlement of the agglomerated coastal population. This makes the migration

of the vulnerable population very challenging, accompanied with high cost and

high level of disruption in economic structure as well.

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In Alexandria, current methods of resistance (Hard Measures) are being

implemented to protect the coastal and built environment. The protection

measures are such as:

Sea walls

Breakwaters

Revetment Blocks

Groins

These measures are introduced to protect the city from storm surges and coastal

inundation. They are all considered resisting hard measures, and if breached

they will cause severe disruption on the coastal community. These are all robust

measures and generate high cost to be maintained and implemented. Also they

have a negative impact on the coastal environment and resulted in continuous

natural degradation, misuse of the natural resources and causing robust and

disengaged relationship between human and the surrounding natural

environment. Besides, they are not aesthetically pleasing.

That is to say, the more the external resistant protection of the community

increases, the more it becomes adapting to resistance and cannot withstand the

external threat. Increasing the resilience means introducing flexible measures

that empowers the community to adapt and be part of the process of

adaptation.

Several examples were presented to soften the existing measures and reduce the

impact of hazard on it.

This is not an indicator that hard measures are better to be avoided. There are

extreme conditions that require the introduction of a resistant hard measure. It

depends on the natural environment.

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This will require early warning systems and adequate actions must be put in

place.

New Motobus, based on the hypothesis, they will be a continuation to the

existing paradigm of top-down planning process, an important change in

paradigm needs to be tackled.

An important change in response needs to take place in approaching new

coastal cities with a more holistic approach, taking into consideration climate

threats of SLR during the initial planning process.

Coastal resilience is the emerging planning paradigm for confronting the

potential climatic change and SLR, is perceived as a natural phenomenon rather

than a threat and not to wait for extreme events in order to start protecting

communities from flooding and using soft measures that can reduce the impact

of climate change and sea level rise and create an interaction between the

natural system and the built community.

In order to become more resilient, there is an urge for cities and regions to

adopt climate change in the initial planning process and design strategies. This

aims at increasing the capacity of the community—its economic, social, and

physical capacity—to better respond to climatic events of flooding

independently of external forces.

The most suitable adaptation strategies for newly developed communities, the

full implication of the climatic issues must be taken into account and it must be

realized that the early presented general strategies of the IPCC of protection,

accommodation and retreat need to be integrated into the initial planning

process. This will happen taking into consideration numerous other non-

climatic measures in the adaptation process which include reversing the

conventional mind-set of mere usage of hard measures and introducing

resilience-oriented thinking. This will require a change in the adaptation

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strategies, like replacing the sea walls by beach nourishment and coastal

vegetation and to re-think of adaptable urban configuration.

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8 List of Figures:

Figure 1 : Author

Figure 2: Author

Figure 3: Nicholls, R.J. and Branson, J. 1998. Coastal Resilience and Planning

an Uncertain Future: An Introduction. The Geographical Journal 164(3), pp.

255-258.

Figure 4: Author

Figure 5: International Panel on Climate Change (IPCC). 2007. Fourth

Assessment report: Climate Change, Synthesis Report.

Figure 6: Nicholls, R.J. and Branson, J. 1998. Coastal Resilience and Planning

an Uncertain Future: An Introduction. The Geographical Journal 164(3), pp.

255-258.

Figure 7: Otto Simonett, UNEP/GRID-Geneva; Prof. G. Sestini, Florence;

Remote Sensing Center, Cairo; DIERCKE Weltwirtschaftsatlas

Figure 8: Otto Simonett, UNEP/GRID-Geneva; Prof. G. Sestini, Florence;

Remote Sensing Center, Cairo; DIERCKE Weltwirtschaftsatlas

Figure 9: Otto Simonett, UNEP/GRID-Geneva; Prof. G. Sestini, Florence;

Remote Sensing Center, Cairo; DIERCKE Weltwirtschaftsatlas

Figure 10:Author produced from GOPP. GIS database of the Nile Delta region.

General Organization for Physical Planning; 2000

Figure 11: Author produced from GOPP. GIS database of the Nile Delta region.

General Organization for Physical Planning; 2000

Figure 12: Author produced from GOPP. GIS database of the Nile Delta region.

General Organization for Physical Planning; 2000

Figure 13: Author produced from GOPP. GIS database of the Nile Delta region.

General Organization for Physical Planning; 2000

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Figure 11 :Author produced from GOPP. GIS database of the Nile Delta region.

General Organization for Physical Planning; 2000

Figure 15: Author produced from GOPP. GIS database of the Nile Delta region.

General Organization for Physical Planning; 2000

Figure 16: Author Adopted from. National Action Plan on Climate 1222 “EEAA”

Figure 17: Author Adopted from International Panel on Climate Change (IPCC).

2001. Technical Summary, Climate Change: Impacts, Adaptation and

Vulnerability.

Figure 18: U.S. Army Corps of Engineers. 2002

Figure 19: CCD 1997 cited by Huettche, C.M., A.T. White and M.M.M. Flores.

2002. Sustainable Coastal Tourism Handbook for the Phillippines. Coasta

Resource Management Project of the Department of Environment and Natural

Resources and the Department of Tourism, Cebu City, Phillippines, pp. 144.

Figure 20: Rotterdam city guide n.d Official website

Figure 21: Klüber Lubrication, Munich 2013 . available from

http://www.klueber.com/en/news/news-detail/2267/ June 28. 2012 [Last

accessed 6-6-2013

Figure 22: Alex. Governorate. 1984. Comprehensive Plan Alexandria 2005;

Final Report. El Shorouk Bookstores Uni Alex., (Translated)

Figure 23: Author60

Figure 24: Author

Figure 25: Figure 25: The World Bank, 2010. Climate Change Adaptation and

Natural Disasters Preparedness in the Coastal Cities of North Africa Phase 1:

Risk Assessment for the Present Situation and Horizon 2030 – Alexandria

Area. Virsion-1

Figure El-Sharnouby B. and Soliman A., 2010

Figure 27: Author

Figure 28: Nordenson G., Seavitt C., Yarinsky A., Cassell,. S,. Hodges, L., Koch.,

M., Smith J., Tantala M. 2009. On the water palisade bay.

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Figure 92 : Sydney Metropolitan Catchment Management Authority and

Department of Environment and Climate Change NSW. 2009. Department of

Environment and Climate Change NSW on behalf of Sydney Metropolitan

Catchment Management Authority.

Figure 30: Sydney Metropolitan Catchment Management Authority and

Department of Environment and Climate Change NSW. 2009. Department of

Environment and Climate Change NSW on behalf of Sydney Metropolitan

Catchment Management Authority.

Figure 31: Hafen City Master PlanFigure 28: Offical Website of HafenCity.

Available from: http://www.hafencity.com/en/glossary-i-m/masterplan.html

Figure 32: MarkusR. 2007. Photo via flicker. Available from:

http://www.flickr.com/x/t/0092009/photos/mrieder/493414849/

Figure 33 : A. Wee 2010 Photo via flicker. Available from:

http://www.flickr.com/x/t/0090009/photos/49111993@N00/4673587687/

Figure 34: sacratomato_hr 2011. Photo via flicker. Available

from: http://www.flickr.com/x/t/0090009/photos/the_h/5836386470

Figure 35: Study Presented by the GOPP on the Nile Delta Coastal

Development (2010)

Figure 36: Author modified from IDG 2010, Study of the Proposal For New

Motobus. Integrated Development Group

Figure 37: Frihy, O.E. and Khafagy, A.A. 1991. Climate and Induced Changes

In Relation To Shoreline Migration Trends at The Nile Delta Promontories,

Egypt. Cremlingen vol. 18, pp. 197 211

Figure 38: IDG 2010 Study of the Proposal For New Motobus. Integrated

Development Group

Figure 39: Watson. D, Adams. M. 2011. Designing for Flooding "Architecture,

Landscape, and Urban Design for Resilience to climate change" John Wiley &

Sons, Inc., Hoboken, New Jersey.

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Figure 40: Watson. D, Adams. M. 2011. Designing for Flooding "Architecture,

Landscape, and Urban Design for Resilience to climate change" John Wiley &

Sons, Inc., Hoboken, New Jersey.

Figure 41: Watson. D, Adams. M. 2011. Designing for Flooding "Architecture,

Landscape, and Urban Design for Resilience to climate change" John Wiley &

Sons, Inc., Hoboken, New Jersey.

Figure 42: Watson. D, Adams. M. 2011. Designing for Flooding "Architecture,

Landscape, and Urban Design for Resilience to climate change" John Wiley &

Sons, Inc., Hoboken, New Jersey.

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List of Meeting

Contact

Person

Field Position Institute Date

Dr.

Mohamed

Asar

Architecture GOPP

Thomas

Abeling

Resilience PHD Student UNO

University

15-12-2012

Abdul

Moneam El

Fiky

Delta

Fragmentation

PHD Student

Urban

Planning

USTUTT

Dr. Abbas El

Zaafarany

Environmental

Design &

planning

Prof. Dr University of

Urban

Planning

Cairo

University

18-

19.02.2013

Mohamed

Salin

PHD University of

Hamburg

Dr. Omar

Badawy

Hydrology Regional

Manager Land

Resources

Programme

CEDARE 5.3.2013

Mrs. Engy Environmental

Science

Head of

adaptation

department

EEAA 17/3/2013

Mrs. Lydia EEAA 17/3/2013

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126

Elwa

Mr. Sherif EEAA

Mr. Ehab

Samir

Civil Engineer Building

Regulations

EEAA

Prof. Dr Kareem Rakha Coastal

Engineer

Cairo

University

Mr. Abdel

Kereem

Coastal

Engineer

Prof. Dr

Mohamed

EL Raey

Environmental

science

Amr Abdel

Megeed

Regional

Program

Manager

Environmental

Governance

and Resilience

Program

CEDARE 14/4/2013

Amed Abdel

Rehim

Regional

Program

Manager

Knowledge

Manager

Programme

CEDARE 14/4/2013

Dr.Medhat Coastal

Reseach

institute

Dr. Essam

Fouad

Coastal

Research

Institute

30/4/2013

Dr. Essam

Fouad

Coastal

Research

Institute

13/5/2013

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Arabic Summary

الخالصة

التغيرات المناخيه هى ظاهره لها تاثير على البيئه و الحياه االجتماعيه بالمناطق الساحليه لدلتا نهر النيل مما

فى . يؤدى الى االحتياج لوضع استراتجيات للحفاظ على البيئه الطبيعيه خاصة مع زىادة التطور و زيادة السكان

يط الساحل عن طرىق نموذج يمثل اسلوب المقاومة و آخر يمثل هذه الدراسه يعرض توجهان للتعامل مع تخط

.اسلوب المرونة فى التعامل مع هذه التغيرات

المرونة يمثل منظومة رد الفعل لمواجهة األحداث الخارجية المتوقعة ويعرض و يشرح تأثر النظم /نظام المقاومة

فى مصر لتبَين أن هناك اختالف فى عدد السكان و لذا تمت دراسة المناطق المهددة على الساحل . الطبيعية بذلك

جد أنه كلما زاد عدد السكان واألنشطة ’النشاط االقتصادى فى المناطق الساحلية المختلفة المنخفضة وبالتالى و

الالقتصادية كان أقل تهديد يؤدي الى اثارة حجم كبير من الفوضى التى تتطلب تدُخل سياسى و مساعدات من

وهذا واضح فى المدن الساحلية المعقدة التركيب و . تمام عمليات نقل البنية التحتية و اعادة التسكينقوى خارجية إل

.لمواجهة آثار ارتفاع منسوب البحر(اساليب المقاومة)المعتمدة على

وبها و مثال على ذلك مدينة االسكندرىة التى تعتبر ذات النصيب االكبر فى تعقيدات التخطيط فهى مقامة بالفعل .

كيانات اجتماعية واقتصادية ونظم للتعامل مع الغمر لمنع اختراق الساحل بالماء باالضافة الى حجم البنية االساسية

و حجم النمو االجتماعى واالقتصادى مما يجعل النظام الحالى ال يستطيع مواجهة تحديات التغيرات المناخية و

مثل ,اسة الحكومة هى التعامل مع الحدث و ليس منع الحدث خاصة ان سي,اكثر مقاومة للتحول الى نظام جديد

( الطرق الصلبة)يستخدم فى مدينة االسكندرىة لحماية الساحل طرق المقاومة ..عمل حاجز للمقاومة لحماية المدن

هذه االسالىب مستخدمة لحماية المدينة من العواصف ...الكتل الخرسانية-كاسرات االمواج-حوائط البحر:مثل

باالضافة الى أنها تستلزم صيانة دورية ذات .نيفة و الغمر و قد يؤدى اختراقها الى اضطراب المجتمع الساحلى الع

و ينتج عنها سوء استخدام للمصادر الطبيعية وتدهور العالقة ,ولها تأثير سلبى على البيئة الساحلية ,تكلفة عالية

لحماية المجتمع ( األسالىب المقاومة )االعتبار أنه كلما زادت مع األخذ فى.بين االنسان و البيئة الطبيعية من حوله

.كلما أصبح أكثر مقاومة للتعايش و ال يستطيع التعامل مع التهديد الخارجى,

يعنى استخدام أساليب أكثر مرونة تجعل المجتمع يستطيع التأقلم و تجعله جزء من ( االساليب المرنة)استخدام

تغذية الساحل :هناك أمثلة عديدة يمكن استخدامها لليونة االساليب الصلبة الموجودة مثل ...عملية التأقلم

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و ذلك لتقليل تأثير ,ن الرملية بطريقة بيولوجيةو تثبيت الكثبا,زيادة المناطق المزروعة على الساحل ,بالرمال

على طول الساحل و تقليل التأثير السلبى المصاحب لألساليب الصلبة و هذا ال يعنى أنه يجب ( الطرق الصلبة)

باإلضافة الى . تجنب الطرق الصلبة ألنه توجد بعض الحاالت التى تستوجب استخدامها وذلك حسب طبيعة البيئة

.حذيرية ورد فعل مدروس و موضوع فى مكانه الصحيحوجود أنظمة ت

لتغيير منهجى متكامل ونظام " مدينة مطوبس الجديدة هى مدينة ساحلية جديدة البد من انشائها من البداية تبعا

مع ضرورة التعامل مع ارتفاع .)شامل يضع فى اإلعتبار التغيرات المناخية و ارتفاع منسوب البحر المتوقع

هذا باإلضافة إلى عدم اإلنتظار حتى حدوث آثار شديدة (, على أنه ظاهرة طبيعىة و ليس تهديد منسوب البحر

يقلل من هذه األثار باإلضافة الى خلق ( األسالىب المرنة)فإستخدام ..تإلغراق إلتخاذ اجراءات الحماية للمجتمع

راتجيات عن طرىق تحليل و هذا يتطلب وضع خطة مبدئية و است, تفاعل بين نظام الطبيعة و المجنمع

استراتيجيات منظمة العامة للحماية و التأقلم و اعادة المعالجة مع األخذ فى اإلعتبار الطرق الغير معتمدة على

( الطرق المرنة )و ادخال ,( الطرق الصلبة)التغيرات المناخىة مثل تغيير العقول التقليدية التى ال تستعمل سوى

.للتفكير

ر فى اإإلستراتجيات التقليدية للتأقلم مثل استبدال انشاء حوائط البحر بتغذية الشواطئ بالرمال و يتطلب تغيي هذا و

زراعة الساحل و هو ما يؤدى الى التأقلم مع التغيرات المناخية و زيادة قدرة المجتمع السكانية و اإلقتصادية و

.البنائية على رد فعل مناسب و بدون مساعدة قوى خارجية

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