A V E H I C L E A L L O C A T I O N M O D E L F O R P O S ......AFET SONRASI ENKAZ KALDIRMA...
Transcript of A V E H I C L E A L L O C A T I O N M O D E L F O R P O S ......AFET SONRASI ENKAZ KALDIRMA...
M A R M A R A U N I V E R S I T Y
I N S T I T U T E F O R G R A D U A T E S T U D I E S
I N P U R E A N D A P P L I E D S C I E N C E S
A V E H I C L E A L L O C A T I O N M O D E L F O R
P O S T - D I S A S T E R D E B R I S R E M O V A L
O P E R A T I O N S
LAMİA GÜLNUR KASAP
MASTER THESIS
Department of Indust r ia l Enginee ring
Thesis Supervisor
Prof . Dr . Özalp VAYVAY
Thesis CO- Supervisor
Assoc. Prof. Dr. Gülfem TUZKAYA
ISTANBUL, 2016
M A R M A R A U N I V E R S I T Y
I N S T I T U T E F O R G R A D U A T E S T U D I E S
I N P U R E A N D A P P L I E D S C I E N C E S
A V E H I C L E A L L O C A T I O N M O D E L F O R
P O S T - D I S A S T E R D E B R I S R E M O V A L
O P E R A T I O N S
LAMİA GÜLNUR KASAP
(524413015)
MASTER THESIS
Department of Indust r ia l Enginee ring
Thesis Supervisor
Prof . Dr . Özalp VAYVAY
Thesis CO- Supervisor
Assoc. Prof. Dr. Gülfem TUZKAYA
ISTANBUL, 201 6
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ACKNOWLEDGEMENT
I would like to present my sincere gratitude to my supervisors, Prof. Dr. Özalp
VAYVAY and especially Associate Prof. Gülfem TUZKAYA for their
stimulating suggestions, valuable contributions, encouraging guidance, support,
endless help and patience through research for and writing of this thesis.
I am grateful to Prof. Talip Alp for accepting to read this thesis and for his
valuable suggestions and precious support.
I would like to give my heartily appreciation to my family; my mother Nevin
KASAP, my father Asst. Prof. Dr. Hüseyin KASAP and my brother Caner Yavuz
KASAP for their persistent help, encouragement, patience, and it will be
impossible to come this day without their support.
I want to thank my lovely friends for their precious support. I really appreciate to
all of you for your great companionship, motivation and advices.
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CONTENTS
ACKNOWLEDGEMENT ................................................................................................. i
CONTENTS ..................................................................................................................... ii
ÖZET ............................................................................................................................. iv
ABSTRACT ..................................................................................................................... v
SYMBOLS ..................................................................................................................... vii
ABBREVIATIONS .......................................................................................................... x
LIST OF FIGURES ......................................................................................................... xi
LIST OF TABLES.......................................................................................................... xii
1. INTRODUCTION ........................................................................................................ 1
2. LITERATURE REVIEW ..................................................................................... 3
2.1. Disaster Operation Management and Humanitarian Logistics ............................. 4
2.2. Disaster Management / Humanitarian Logistics Categories................................. 7
2.2.1. Pre-disaster categories ............................................................................................ 9
2.2.1.1. The preparation phase .......................................................................................... 9
2.2.1.2. The mitigation phase ......................................................................................... 10
2.2.2. Post-disaster categories......................................................................................... 10
2.2.2.1. The response phase ............................................................................................ 11
2.2.2.2. The recovery phase ............................................................................................ 11
2.3. Applications in Turkey: Previous Studies .......................................................... 12
2.4. Debris Removal Operation ................................................................................. 12
2.4.1. Debris recycling operation.................................................................................... 16
3. PROBLEM DEFINITION AND SOLUTION APPROACH ............................. 17
3.1. Solution Approach .............................................................................................. 18
3.2. General Structure and Formulation of Model ....................................................... 1
3.3. Modeling Challenges ............................................................................................ 9
3.4. Estimation of Input Data ..................................................................................... 10
3.4.1. Test data set...................................................................................................... 15
3.5. Results and Analysis ........................................................................................... 16
4. CONCLUSIONS ........................................................................................................ 19
REFERENCES ............................................................................................................... 20
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APPENDIX ................................................................................................................................25
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ÖZET
AFET SONRASI ENKAZ KALDIRMA OPERASYONLARI İÇİN
BİR ARAÇ ATAMASI MODELİ
Afetin insan, doğa, ekonomi ve sosyal yapı üzerindeki etkilerini azaltmak için
hazırlanan afet operasyon yönetimi planları çok ciddi bir öneme sahiptir. Afet
operasyon çalışmaları; müdahale ve iyileşme evrelerindeki çalışmaların sürelerini
kısaltmak, operasyon maliyetlerini azaltmak ve daha koordineli olan yeni teknikler ile
birlikte yeni planlar oluşturmak açısından özellikle son zamanlarda önemini gittikçe
arttırmıştır. Enkaz Kaldırma Operasyonları da afet operasyon çalışmalarının bir konusu
olarak bu bağlamda önem kazanmıştır.
Enkaz operasyon planları depremden hemen sonra başlar. Diğer yandan, enkaz kaldırma
operasyonları, arama kurtarma çalışmaları tamamlandıktan sonra başlar. Enkaz kaldırma
operasyonları afet sonrası kategorisi ve iyileştirme evresi çalışmalarından biridir. Afet
operasyonları yönetiminde, enkazın afetzedeler üzerindeki negatif etkisi ve çevresel
etkilerinden dolayı olabildiğince çabuk kaldırılması çok önemlidir. Enkazın toplanması
işleminden sonra doğru bir şekilde bertaraf edilmemesi ya da geri dönüşümün
yapılmaması durumunda ileriye yönelik yer altı kaynaklarına, toprak ve havaya ciddi
zararları bulunmaktadır.
Bu çalışmada, Sakarya ili afet sonrası enkaz temizleme problemi için araç
lokasyonlarından depremden etkilenen bölgelere ve geçici depolama bölgelerine araç
atama modeli önerilmiştir. Ayrıca modelde enkazın geri dönüşüm işleminin
yapılabileceği geçici depolama alanlarının açma kapama kararları da bulunmaktadır.
Önerilen matematiksel model (i) enkaz kaldırma operasyonlarının toplam maliyetini, (ii)
enkazın etkilenen insanlar üzerindeki negatif etkisini ve (iii) atanan araçların emisyon
indeksini en küçüklemeyi hedefleyen üç amaçlı bir modeldir. Lingo optimizasyon
programı ile çözdürülen çok amaçlı modelin amaç fonksiyonlarını birleştirerek çözmek
için Lineer Fiziksel Programlama tekniğinden yararlanılmıştır. Çözüm sonucunda tüm
amaç fonksiyonları ideal aralıkta bulunmuştur.
Anahtar Kelimeler: Enkaz Kaldırma, Afet Operasyon Yönetimi, İnsani Yardım
Lojistiği, Araç Atama, Lineer Fiziksel Programlama
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ABSTRACT
A VEHICLE ALLOCATION MODEL FOR POST-DISASTER
DEBRIS REMOVAL OPERATIONS
Disaster operation plan is of vital importance in reducing the effect of disaster on human
beings, natural environment, national economy and social structures. The new
technologies developed recently which, have shortened the time taken for the tasks
undertaken in the stages of intervention and improvement, and have resulted in
minimizing operational costs, and bringing in new techniques of coordination have
rendered the importance of the disaster operation studies has increased steadily,
especially in recent times. Debris Removal Operations as a subject of the disaster
operation studies has become more important in this context.
Disaster Operation Plans start immediately after disaster occurs. On the other hand,
debris removal operations start after search and rescue operations are being completed.
They are after-disaster and recovery phase activities. The debris need to be gathered as
quickly as possible in order to ease the negative impact of the catastrophe on the
affected people and nature. If Debris is not recycled or disposed off promptly and
properly after the collection process, may cause environmental pollution (water
resources, soil and air).
In this study, in order to address the debris removal problem, a mathematical model has
been proposed to assign the debris removal vehicles from locations of the vehicles to
the affected districts of Sakarya and predetermined temporary storage areas. The model
is also capable of making rational decisions for opening temporary storage areas,
designed for recycling the debris. The mathematical model has employed in this study
three objectives: (i) minimization of operational costs, (ii) mitigation of the negative
impact of the disaster on the affected people, and (iii) minimization of the emission
index of the assigned vehicles. Linear Physical Programming technique is used to
combine the three objective functions of the multi objective model and Lingo
optimization software is used to run the proposed model. As a result of the proposed
model’s solution, all objective functions are found in ideal range.
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Key Words: Debris Removal, Disaster Operation Management, Humanitarian Logistics,
Vehicle Allocation, Linear Physical Programming
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SYMBOLS
i : Disaster-affected area
j : Vehicle location
k : Temporary storage area
t : Time period
p : Process type
d : Disposal area
e : Emission index
𝑿𝟏𝒋𝒊𝒆𝒕 : The amount of excavator with e emission index is assigned from vehicle
location j to disaster affected area i at time period t
𝑿𝟐𝒋𝒊𝒆𝒕 : The amount of loader with e emission index is assigned from vehicle location j
to disaster affected area i at time period t
𝑿𝟑𝒋𝒊𝒆𝒕 : The amount of truck with e emission index is assigned from vehicle location j
to disaster affected area i at time period t
𝑿𝟒𝒋𝒌𝒆𝒕 : The amount of loader with e emission index is assigned from vehicle
location j to temporary storage area k at time period t
𝑿𝟓𝒋𝒌𝒆𝒕 : The amount of truck with e emission index is assigned from vehicle
location j to temporary storage area k at time period t
𝒁𝒊𝒌𝒆𝒕 : The amount of truck with e emission index transport the debris from affected
area i to temporary storage area k at time period t
𝒁𝟏𝒌𝒅𝒆𝒕 : The amount of truck with e emission index transport the debris from
temporary storage area k to disposal area d at time period t
𝝁𝒌 : Decision of opening temporary storage area k (0;1)
𝑸𝒌𝒕 : The amount of debris in the temporary storage area k at time period t
𝒈𝒅𝒎𝒌𝒕 : The amount of recycled debris in temporary storage area k at time period t
𝒈𝒅𝒑𝒎𝒌𝒑𝒕 : The amount of recycled p type debris in temporary storage area k at time
period t
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𝒂𝒊𝒕 : The amount of debris remaining in the affected area i at time period t
𝒂𝟏𝒊𝒕 : The destruction amount remaining in the affected area i at time period t
𝒕𝒎𝒊𝒌𝒊𝒌𝒕: Debris transported from to disaster affected area i to temporary storage area k
at time period t
𝒕𝒎𝒌𝒌𝒅𝒕: Debris transported from to temporary storage area k to disposal area d at time
period t
𝒎𝒋𝒊 : The cost of assigning process of vehicles from vehicle location k to affected
area i
𝒎𝟏𝒋𝒌 : The cost of assigning process of vehicles from vehicle location k to temporary
storage area k
𝒇𝟏𝒋𝒆 : The amount of excavator with e emission index at vehicle location j
𝒇𝟐𝒋𝒆 : The amount of loader with e emission index at vehicle location j
𝒇𝟑𝒋𝒆 : The amount of truck with e emission index at vehicle location j
𝒄𝟏 : Capacity of each excavator in the vehicle location
𝒄𝟐 : Capacity of each loader in the vehicle location
𝒄𝟑 : Capacity of each truck in the vehicle location
𝒄𝒌𝒌 : Capacity of temporary storage area k
𝒅𝟏𝒌𝒅 : Distances between temporary storage area k and disposal area d
𝒅𝟐𝒊𝒌 : Distances between disaster affected area i and temporary storage area k
𝒅𝟑𝒋𝒊 : Distances between vehicle location j and disaster affected area i
𝒅𝟒𝒋𝒌 : Distances between vehicle location j and temporary storage area k
𝒂𝒂𝒊 : The estimated amount of debris at disaster affected area i
𝒂𝒂𝟏𝒊 : The estimated amount to be demolition at disaster affected area i
𝜹𝒌𝒑 : Debris ratio for process p which can be done at temporary storage area k
𝒈𝒑 : income derived from process p
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𝝋𝒌 : Cost of opening / closing temporary storage area k
𝝋𝟏𝒌 : Recycling processing cost at temporary storage area k
𝒏𝟏 : Demolishing costs
𝒏𝟐 : Loading / unloading costs
𝒏𝟑 : Transportation costs
𝒏𝒆𝒊 : Population ratio of i location
𝒏𝒊𝒓𝒂𝒕𝒆𝒕 : Negative impact rate on i location at t time
𝒆𝒅𝒆 : Emission penalty of e emission index
B : Fuel costs
Rje : Vehicle usage cost has to e emission index in j vehicle location
x
ABBREVIATIONS
OR : Operation Research
AFAD : The Disaster and Emergency Management Authority
İSTAÇ : İstanbul Büyükşehir Belediyesi Çevre Koruma ve Atık Maddeleri
Değerlendirme Sanayi ve Ticaret A.Ş.
GIS : Geographical Information System
TUİK : Turkish Statistical Institute
TSA : Temporary storage areas
OF : Objective Function
LPP : Linear Physical Programming
DAS : Disaster Affected Site
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LIST OF FIGURES
Figure 1.1. Disasters’ types and inputs/outputs (modified from Can, 2005) ................... 3
Figure 2.1.1. Challenges of humanitarian logistics (Kova´cs and Spens, 2009) ............. 5
Figure 2.1.2 Stakeholders in Humanitarian Logistics (Wisetjindawat et al., 2014) ........ 6
Figure 2.1.3. Phases of relief efforts (Wisetjindawat et al., 2014) .................................. 6
Figure 2.2.1. Categories and Phases of Disaster / Humanitarian Logistics ..................... 7
Figure 2.4.1 An image of an uncontrolled disposal of debris (T.C. Tekirdağ Valiliği İl
Çevre ve Orman Müdürlüğü) ......................................................................................... 13
Figure 2.4.2 Categories and Phases of Debris Management (Modified from Şahin,
2013) ............................................................................................................................... 15
Figure 2.4.1.1 Basic approach of Debris recycling operation (Öztürk, 2005) ............... 16
Figure 2.4.1.2 Combined approach of Debris recycling operation (Öztürk, 2005) ....... 16
Figure 2.4.1.3 Approach of Debris recycling operation with using recycling machines
(Öztürk, 2005) ................................................................................................................ 16
Figure 2.4.1.4 Recycling machines are used at facility in Istanbul (İSTAÇ) ................ 17
Figure 3.1.1. Class functions for linear physical programming (Maria et al., 2003) .... 20
Figure 3.2.1. Problem definition ...................................................................................... 2
Figure 3.4.1. DASs , TSAs, location of vehicles, disposal sites and their relations ...... 12
Figure 3.4.2. Penalty of e emission index ...................................................................... 14
Figure 3.5.1. Lingo screen of the proposed model by using input data ......................... 17
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LIST OF TABLES
Table 2.2.1. Pre-disaster and Post-disaster Activities of Humanitarian Logistics
(Gösling and Geldermann, 2014) ..................................................................................... 8
Table 2.2.1-continue Pre-disaster and Post-disaster Activities of Humanitarian Logistics
(Gösling and Geldermann, 2014) ..................................................................................... 9
Table 2.2.1.1.1. Topics of Pre-Disaster (Güler, 2005) ................................................... 10
Table 3.4.1. Weights of objective functions ................................................................... 10
Table 3.4.2. Quantity of demolished and heavily damaged buildings ........................... 11
Table 3.4.3. Capacity of vehicles and cost of work ........................................................ 13
Table 3.4.4. Quantity of excavator, loader and truck at location of vehicle j ................ 13
Table 3.4.5. The sales prices of recycled materials ........................................................ 14
Table 3.4.6. The recycling rates of debris ...................................................................... 15
Table 3.4.1.1. The amount of debris, the numbers of demolished buildings and
population rates............................................................................................................... 15
Table 3.4.1.2. The distances between locations ............................................................. 16
Table 3.4.1.3. Test set’s quantity of excavator, loader and truck at location of vehicle j
........................................................................................................................................ 16
Table 3.5.1. The preference ranges of the case study ..................................................... 17
Table 3.5.3. Normalized weight deviations of objectives .............................................. 17
Table 3.5.4. The numerical analysis ............................................................................... 18
Table 3.5.5. Quantity of assigned excavator, loader and truck from location of vehicle j
to DAS i and TSA k ........................................................................................................ 18
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1. INTRODUCTION
Disaster is a sudden and unexpected event which has a phenomenally negative impact
on people, environment and economy due to the massive destruction, caused in terms of
loss of life and property. Hence, significance of the work done in this regard can hardly
be emphasized. Disaster Operation Management activities are used to reduce the
detrimental effects of the disaster on people, material, social welfare, wealth and human
casualties. Such studies focus on identifying locations of suitable disaster logistics
centers and evacuation facilities, the position of responders and facility location
assignments between facilities, preparing strategic plans for search and rescue
operation, transforming the victims from disaster affected area to shelters, emergency
relief operations, etc. In order to coordinate these activities, disaster operations deal
with three categories of events classified as “pre-disaster”, “during disaster” and “post
disaster”, developments divided into four phases named “mitigation”, “preparation”,
“response” and “recovery”.
Of the disaster operation management activities, the post-disaster activities have high
uncertainty since it is difficult to establish the exact time and location of the disaster, the
size of the destruction and uncertain demand. Operation Research (OR) methods are the
most common decision analysis and quantitative methods the used to eliminate. OR
methods offer a systematic approach to find the optimal or nearly optimal solution and
scenario analysis might be used to eliminate the uncertainties.
Through implementing well-designed post-disaster plans, both ensuring the
coordination between activities and using time efficiently, losses would be minimized.
Efficient time management and scheduling of activities are important for all post-
disaster plans and alleviation of the negative impact on the victims. From this point of
view, post-disaster studies may have multiple objectives. Hence, an effective solution
for the purpose of identifying priorities can be provided by using the normalization
methods.
It has been argued in recent years that urban transformation of civil structures, i.e.
reconstruction of very old buildings, possibly affected by previous earthquakes, with
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diligent planning can contribute significantly to the reduction of debris and negative
impact on the victims with using time effectively.
In this thesis, the debris removal problem was focused in order to use time efficiently
and reduce the negative impacts on people and environment for the case of the
earthquake in Sakarya. As a result of the existing literature investigation, studies on the
collection and disposal of debris have been found, on the other hand the study on the
recycling process of the debris has not been found. In the most of the studies, problem is
investigated as arc routing problem.
As in all phases on life, in case of disaster, limited resources coupled with huge and
fatal emergencies require the available resources to be used efficiently in a highly
number of coordinated manner. Whitin this context assignment of limited number of
vehicles from vehicle locations to the disaster affected areas and temporary storages
assume vitally importance. Also if the debris is not collected with appropriate and
accurate methods, the land, underground water and the surrounding environment may
become contaminated. Improperly stacked debris can cause various hazards including
environmental pollutions such as land, air quality, and water system. Additionally, pose
serious danger citizens who attempt to recover recyclable scrap without any permission.
Considering these situations, a mathematical method is proposed in order to spend
efficiently time, reduce the negative impact on victims and on the environment
(emission index). Linear Physical Programming technique is used to combine the multi
objectives function. The data used in the model is created based on Sakarya district of
Turkey. On the other hand, the smallest input data are used to solve the proposed model
because of the solution time of the real case input data. Following the introductory
section of this thesis, a comprehensive literature review is carried out in the second
section. Problem definition and solution approach is treated in the third section where
Solution approach, definition of the general structure and formulation of the model and
the results of the pertinent analysis is presented. Here in the last section comprises
conclusions and include proposals from future research of the study and a generalized
summary of the results welded by the proposed model.
3
2. LITERATURE REVIEW
Disaster is a shocking event and caused by nature, technologies and human. It contains
high levels of uncertainty because of difficulty to detect location and time and severely
damages functioning of a community or society by causing human, material and
economic or environmental losses that cannot be accomplished by using local resources
(Caunhye et al., 2012; Galindo and Batta, 2013; Ersoy and Börühan, 2013; Gösling and
Geldermann, 2014; Holguín-Verasa et al., 2013; Özdamar and Ertem, 2014;
Wisetjindawat et al., 2014). Disaster types and disaster inputs/outputs are seen in Figure
1.1.
Figure 1.1. Disasters’ types and inputs/outputs (modified from Can, 2005)
As a result of the definition to decide whether or not a situation is a disaster, the
following three are questions of great importance.
1) Does the event have a badly destructive effect on the functioning of a society?
2) Are the local resources enough in order to deal with effects of the event?
3) Are non-local agencies needed to get involved through a conventional or non-
standard procedure?
An airplane crash is the most common example of this decision. When this case
investigates the idea of this questions, it is not a disaster because it can be conduct by
local agencies with standard procedures. On the other hand, if a terrorist attack is the
DISASTERS
Natural Disasters
Man-Made or Technological
Disasters
Drought
Flood
Landslide
Volcanic Eruption
Earthquake
Tornado
Hurricane Nuclear and Chemical Accidents
Huge fire
War Illegal
Construction
Dam brake
Terror
Lack of Energy or Resources
Limited Resources
Huge Demand
Fatal Emergencies
Human Losses
Material Losses
Economic/Environmental
4
reason of the crash, then it would be called a disaster because this case requires the
support of numerous organizations including organizations in the country (Galindo and
Batta, 2013).
2.1. Disaster Operation Management and Humanitarian Logistics
Disaster operation management is a set of activities that reduce the effect of the disaster
on the economy and human casualties. It is used to return the society to its normal
situation (Galindo and Batta, 2013). Disciplines of logistics management, project
management, risk management, operation research, and resource usage techniques,
information management systems, geographical systems etc. are the most popular ones
to predict and deal with the disaster effects.
As in all phases of life, in case of disaster, resources are limited and demands are huge
and emergencies fatal, so that available resources must be used efficiently and in a
coordinated manner. In this phase integrated disaster management (IDM) system is used
to coordinate all these resources. The basic principles of the IDM are (Can, 2005);
Research all risks,
Apply all phases,
Use all resources efficiently,
Ensure that all the individuals and organizations participate (public institutions
and organizations, non-governmental organizations, population)
Humanitarian logistics deals with activities to reduce health, material and wealth
problems which occur such as destruction of emergency facilities, communicable
diseases, supply of water, food and energy. Examples of these activities are
determination of emergency relief facility location, planning of the distributions of the
relief items, determination of the evacuation centers location, building these evacuation
centers and transportation of the emergency needs and similar products to the required
location and the person, on required time (Börühan et al., 2012; Ersoy and Börühan,
2013; Holguín-Verasa et al., 2013). The most important rule of humanitarian logistics is
the right material is delivered to the right person, in the right amount, the right way, at
the right time and the right place (Tanyaş et al., 2013).
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Differences of humanitarian logistics from business logistics are summarized as
follows:
Unpredictability of requirement, under the time, location, variety, and dimension
constraints (Kova´cs and Spens, 2009);
Uncertainty of networks (Holguín-Verasa, et al., 2013);
Suddenness of the event of requirement in high quantity however with short lead
times for an extensive variety of supplies (Kova´cs and Spens, 2009);
The efficiency is related with the timeliness of dispatch (Kova´cs and Spens,
2009);
An absence of resources in circumstances of supply, human, technology,
transportation capacity, and money (Kova´cs and Spens, 2009);
Neutral pursued (Holguín-Verasa, et al., 2013);
Lose its significance of cost minimization applications which are especially
done for during disaster (Tanyaş et al., 2013).
A conception model can be used to identify the challenges faced in humanitarian
logistics problem at the beginning of the project and this model is seen in Figure 2.1.1
(Kova´cs and Spens, 2009).
Figure 2.1.1. Challenges of humanitarian logistics (Kova´cs and Spens, 2009)
Humanitarian operations have complex structure because of some factors such as the
following (Wisetjindawat et al., 2014):
Disaster Types
Focus and location of the
humanitarian organization
Stakeholder environment
• Disaster cause (natural/man-made)
• Warning time (cost)
• Probability of disaster in the region
• Mandate related to phase of relief
• Regional presence
• Dependence on declaration of state
• Internal etc., external challenges • Relevant other organizations
Identify challenges
based on
Dimensions
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1) Numerous different actors like volunteers, victims, governmental and non-
governmental agencies, and logistics companies (see Fig. 2.1.2).
Figure 2.1.2 Stakeholders in Humanitarian Logistics (Wisetjindawat et al., 2014)
2) Distinct phases of relief efforts like the first one is minimum requirements for
survival, second one is some victims are able go back to their homes while some
victims whose houses were seriously damaged still remain at shelters. The third phase is
when most victims are able to go back home but some need to stay longer and are
moved to temporary houses. For the fourth phase, although victims have resumed
normal life, they still need some support in order to restore their quality of life faster;
there are still some donors wishing to provide support (see Fig. 2.1.3).
3) Particular resource requirements (including materials, goods, and people).
Figure 2.1.3. Phases of relief efforts (Wisetjindawat et al., 2014)
All this complexity should be taken into account in the overall planning and operation
of humanitarian logistics, to make them smarter, faster, more reliable and also no more
Donors
Victims
Government Agencies
Non-Government Agencies
Logistics Companies
Phase
1
Phase
2
Phase
3
Phase
4
Need
s o
f vi
ctim
s
Disaster Life at shelter Life at temporary house Normal life
Time
Interactions
7
expensive than necessary. In addition, time constraints in humanitarian logistics during
survival period are more crucial than usual, because faster relief operations mean a
greater likelihood of saving lives (Wisetjindawat et al., 2014).
2.2. Disaster Management / Humanitarian Logistics Categories
Disaster operations and humanitarian logistics are tackled in three categories is pre-
disaster, during disaster, post-disaster activities. They consist of including four phases
mitigation, preparation, response and recovery. Preparation and mitigation are the pre-
disaster phases which importantly decrease the economic, social and physical effects of
a disaster. The examples of these phases are pre-positioning of critical supplies,
improvement of structures, and the development of response plans. Response and
recovery are the post-disaster phases. Determination of the pre-disaster preparation and
planning the coordination of the post-disaster activities have vital importance in easing
uncertainties and reducing huge casualties which occur after the disaster. After disaster,
management of search and rescue operations, health care services, shelter, debris
removal, and logistics of the demands in limited time is very important (Caunhyeet al.,
2012; Galindo and Batta, 2013; Ersoy and Börühan, 2013; Gösling and Geldermann,
2014; Holguín-Verasa et al., 2013; Özdamar and Ertem, 2014; Wisetjindawatet al.,
2014). The disaster relief process can be seen as a cycle linking the recovery and
preparedness phases as seen in figure 2.2.1 (Kova´cs and Spens, 2009).
Figure 2.2.1. Categories and Phases of Disaster / Humanitarian Logistics (Modified
from Kova´cs and Spens, 2009)
Preparation
Mitigation
Response
Recovery
Pre-Disaster
Post-Disaster During Disaster
8
A wide range of humanitarian logistics activities comprises post disaster activities. The
planning of post disaster activities and the need to create a network derive from a
number of requests to eliminate the negativity that may arise after the disaster.
Examples of these activities; comprise allocation of temporary warehouses in bigger
cities, distribution centers and drop-off points, determination of network which include
such activities like plans of decreasing the errors of logistics network where transport
corridors may be broken, unsafe or insecure, planning and implementation the
communication network between operational units (private sector, specialized
military/non-military institutions, government agencies, The Disaster and Emergency
Management Authority (AFAD)). Pre-disaster and post-disaster activities are seen in
table 2.2.1 (Gösling and Geldermann, 2014).
Table 2.2.1. Pre-disaster and Post-disaster Activities of Humanitarian Logistics
(Gösling and Geldermann, 2014)
Pre-disaster activities Post-disaster activities
Determining the location of permanent
warehouses, suppliers and the material
to be stored.
Determining the type, quantity,
capacities, locations, and suppliers of
the transportation vehicles.
Determining the location and the
number of professional man power.
Determining the routes and the
schedules for evaluation teams
Determining the location, capacities
of permanent warehouses and
distribution centers and material to
be stored in there.
Determining the locations of
delivery points in the affected
settlements
Determining the locations of non-
priority donation’s separation
centers.
Determining the quantities and the
location of the professional and
volunteer workers.
9
Table 2.2.1-continue Pre-disaster and Post-disaster Activities of Humanitarian
Logistics (Gösling and Geldermann, 2014)
Pre-disaster activities Post-disaster activities
Identification of suppliers and
supply orders for relief materials.
Determining the types, loads, routes
and schedules of delivery vehicles
2.2.1. Pre-disaster categories
Pre-disaster activities are long or short term activities that exercise instrumental role in
strategic planning or disaster mitigation. These activities aim at reducing the devastating
effects of disasters and protecting the health and wealth of the communities (Can,
2005). Examples of this category are facility location, stock pre-positioning, evacuation,
training, determining unsuitable constructions, etc. (Caunhye et al., 2012). The main
purpose of preparedness plans and risk-prevention actions is to reduce the destructive
effects of the disaster. Stochastic models are used due to the high level of uncertainties
such as the impact level, time and location of disaster (Wisetjindawat et al., 2014).
2.2.1.1. The preparation phase
The aim of the preparation phase is to take corrective action in order to alleviate or
eradicate the impact of the disaster on community in the most proper way and the most
efficient organizations and procedures on time (Can, 2005). Building codes, education
and practice and insurance regulations related to land usage are the examples for this
phase. Preparation of disaster starts with risk analysis and damage visibility which are
used to plan the disaster relief operations efficiently. This is followed by planning
studies, evaluating information systems, planning the efficient use of resources and
facilities and determining the location of new facilities. If a problem occurs, warning
system generates the disaster response mechanism and planning the public awareness
education in order to prepare the people for disaster and help them understand the
mechanism. Last but not least, “practice” is prerequisite to better coordination and
10
reducing mistakes during action (Wisetjindawat et al., 2014). This system is illustrated
in Table 2.2.1.1.1.
The efficiency of disaster relief operations is very dependent on the quality of the
activities which are carried out the preparation phase. This is taken to mean that the rate
of saving lives increases with efficient use of resources. Success of disaster
preparedness is scaled with estimating the requirements of survivors, and the estimated
capacities of the planned supply chains. This preparation helps to have information
about such as the capacities of facilities, and the coordination plan availability about
vehicles and personnel. So that, these activities can be quickly organized with these
plans on recovery phase (Wisetjindawat et al., 2014).
Table 2.2.1.1.1. Topics of Pre-Disaster (Güler, 2005)
Preparation of
disaster
Risk Analysis and
Damage Visibility Planning Studies Institutional Studies
Information Systems Resources and
Facilities Warning Systems
Disaster Response
Mechanisms
Disaster Awareness and
Public Education Practice
2.2.1.2. The mitigation phase
The Mitigation phase starts after the activities of recovery and rebuilding phases, and
continues until a new event occurs. All precaution any activities should be carried out
during this phase in order to prevent the effect of disaster and huge causalities. The
activities of this phase are training and practice, reviewing the procedures of the during
disaster category, reviewing building and the earthquake regulations, insurance
activities, etc. (Can, 2005)
2.2.2. Post-disaster categories
Post disaster category of activities commences immediately after a disaster has
occurred. This category is subdivided into long-term and short-term activities. This
category starts with the response phase activities which starts immediately after a
11
disaster and continues until the end of the recovery phase (Özdamar and Ertem, 2014;
and Can, 2005).
2.2.2.1. The response phase
The aim of this phase is to enhance survival of the injured people, ensuring the
treatment of the injured and the provision of the minimum requirements of basic
necessities such as water, food, clothes, sheltering, and security. Search and rescue
operations, allocation of vehicles and emergency needs, relocation of disaster victims,
impact assessment activities, and investigation of the required repairs are the activities
of this phase (Özdamar and Ertem, 2014; and Can, 2005).
Depending on the size of the disaster, these activities are carried out in one or two
months.
Logistics models for the response phase are reviewed in two major categories:
a) Relief delivery/casualty transport models,
b) Mass evacuation models. (Özdamar and Ertem, 2014; and Can, 2005)
2.2.2.2. The recovery phase
The aim of the recovery phase is to make all the efforts required for communities
affected by the disaster to attain and sustain a minimum level of vital activity such as
communication, transportation, water services, energy, sewerage services, education,
long-term temporary housing, economic and social activities, etc. (Can, 2005).
This phase consists of short term and long term activities. During short term activities,
chaotic and challenging situations exist because needs are extreme and resources are
limited. The volunteer management, debris removal, the restoration of critical
infrastructure, procurement of materials and their distribution take place during this
term. On the other hand, the goal of the long term recovery activities is to return to
normal way of life. The delivery of food and medicines to affected areas is the activity
of this phase (Holguín-Verasa, et al., 2013).
12
2.3. Applications in Turkey: Previous Studies
Disaster management and disaster / humanitarian logistics issues have found huge space
in the pertinent literature which focuses on studies relevant to Turkey. Literature on the
subject is researched and after the classification study (see in the Appendix 1 and
Appendix 2), gaps in the literature covering issues for Turkey were investigated.
Disaster management and disaster / humanitarian logistics issues of implementation is
observed mostly the studies concerning İstanbul or Ankara. Comprehensive studies
need to be done for other regions associated with risks. In terms of the type of disaster,
only the earthquake issue was studied. Clearly other topics associated with very high
risks for Turkey such as floods, terrorism, possible problems related to energy sources,
etc. cannot be ignored. Studies on certain issues such as volunteer management,
allocation and coordination of search and rescue teams, efficient usage of resources
such as assigning vehicles for debris removal case have been found to be lacking.
2.4. Debris Removal Operation
Debris removal operations start after search and rescue operations are completed. They
are post-disaster, recovery phase activities. They are complex problems because of huge
demand and high level uncertainty which is due to the difficulties associated with
making reliable estimation of the size of destruction is real terms. Considering the large
amount of debris waste produced after disasters debris removal management assumes
vital importance due to its impaction on the environment and the health of residents
exposed to it. If the debris is not collected with appropriate and accurate methods, the
land, underground water and the surrounding environment may become contaminated.
Improperly stacked debris can cause various hazards including environmental pollutions
such as land, air quality, and water system. Additionally, pose serious danger citizens
who attempt to recover recyclable scrap without any permission (Hu and Sheu, 2013;
Palabıyık, 2000; T.C. Tekirdağ Valiliği İl Çevre ve Orman Müdürlüğü).
Debris has different characteristics depend on the nature of event such as renovation,
construction, demolition activities and disaster. Although components of construction
and demolition waste vary depending on the content of the materials used in
construction, debris is produced from reinforced concrete, concrete, brick, cinder block,
13
briquette, wood, glass, metal (steel, aluminum, copper, brass, iron), plaster, drywall,
tile, plastic, electrical components, pipes. Reinforced concrete, concrete, cinder block,
briquette are used as aggregate for some type of applications after breaking and
crushing operations which are time consuming and expensive processes. However, this
recycling process preserves primary aggregate resources and considerably diminishes
pollution effects on the environment of affected sites. If debris is stacked without any
systematic procedure at landfill, soil may be contaminated resulting in prevention of
plant growth in that area. Similarly, debris deposited on river, batches can cause the
narrowing and changing of the riverbed. When discharged near roads debris can cause
bad view, pollution of soil and blockage of channels (Hu and Sheu, 2013; Palabıyık,
2000; T.C. Tekirdağ Valiliği İl Çevre ve Orman Müdürlüğü). Figure 2.4.1 illustrates
such a bad practice.
Many countries have banned the uncontrolled disposal of such waste. Since the
aggregate resources are limited, especially the use of construction and demolition waste
as secondary raw materials should be encouraged in Turkey. Also the cleaning process
of uncontrolled pouring of debris means extra cost and manpower (Hu and Sheu, 2013;
Palabıyık, 2000).
Figure 2.4.1 An image of an uncontrolled disposal of debris (T.C. Tekirdağ Valiliği İl
Çevre ve Orman Müdürlüğü)
Another important aspect of the disaster management is debris operations. Pre-disaster
activities are of great significance since they may be designed to reduce the cost of
debris removal operations. Pre-disaster debris removal operations start with estimation
14
of debris size by using special techniques. Removal operations are followed by
preparation of debris collection, reduction /recycling and final disposal strategies and
procedures: Finally, debris management site planning is accomplished. Training of
debris management teams are important for the proper implementation of the processes
identified in the planning during pre-disaster, mitigation phase. Building inspections are
vital importance, since through too in order to this practice leading to due measures the
size of destruction can be considerably reduced. Immediately after disaster, Debris
management sites operations and debris clearance start concurrently, search and rescue
operations must begin rapidly and effectively. Pre-disaster activities have important
roles to achieve effective debris management sites operations which depend on the
appropriate, timely and quick coordination of teams. Clearing debris from emergency
routes is an operation which need to be done as fast as possible since human life is
concerned. While debris clearance is a response phase activity, debris management site
operations start at the response phase and continue during the recovery phase too.
Debris collection, recycling, and final disposal operations are also a part of debris
management site operations. Categories and Phases of debris operations are depicted in
Figure 2.4.2 (Hu and Sheu, 2013; Şahin, 2013).
When examining international practices highly successful operations the case of the Los
Angeles earthquake which took place on January 17, 1995. Stands out Los Angeles city
debris management strategies helped reduce the cost of debris removal operations.
About 76 percent of the debris was recycled so that 4445000 cubic meters of landfill
were saved. The debris management strategies have three important rules (Palabıyık,
2000);
1. Dissemination of information: man power for debris removal process was
educated regarding what should be done after disaster. Debris collection process
was conducted with the orientation of the phone calls from debris removal and
transfer companies and citizen.
2. Recycling: Every citizen is obligated to recycle his/her own debris. Failing to do
that the recycling companies are allowed to do the job. The effort of the local
people provides a reduction of the debris removal cost and increase
effectiveness.
15
3. Exchange of materials: Some community groups have been employed by the
city administration of Los Angeles for the separation process of bricks, iron and
wood from debris. This is especially attractive for lots income people who can
use these materials for their own business.
Figure 2.4.2 Categories and Phases of Debris Management (Modified from Şahin,
2013)
While international operations subject to the best practices, it has attracted the attention
of a certain section of society in our country. When previous national operations are
examined, it is understanding that new more coordinated and prepared debris
management site plan is needed. After Erzincan earthquake on March 13, 1992, debris
was poured uncontrolled near roads, around town that may be detrimental to the
environment and blocked traffic. Debris operations were acted in that vein after
Marmara earthquake on August 17, 1999. Construction and rubble wastes were poured
into the sea, the river reaching the sea and regularly on different areas at Değirmendere
landfill, Izmit. Debris removal operations were tendered to 10 subcontractors in
Pre-Disaster Preparation
Post-Disaster Response
Post-Disaster Recovery
Estimation of
debris and scenario analysis
Debris Clearance Debris Collection
Procedures and strategies of
collecting debris operations
Debris Management Sites Operations
Debris Management Sites Planning
Debris Reduction / Recycling
Debris Final Disposal
Pre-Disaster Mitigation
Team Training
Building inspections
Team Drill
16
Sakarya. In the first days following the disaster, they were poured uncontrolled way
near Sakarya River and part of swamp areas which are determined by province. Most of
citizen who attempted to separate iron from stack on debris final disposal area were in
danger because of uncontrolled access to the area (Palabıyık, 2000).
2.4.1. Debris recycling operation
Debris recycling operation may become necessary in order to conserve primary
aggregate resources and reduce the harmful effect on environment associated with
debris. In fact cost of debris removal operations can be relatively decreased by well-
planned recycling operations as in the Los Angeles example. The techniques for
collecting, recycling and final disposal of construction and demolition waste are shown
in Figure 2.4.1.1, 2.4.1.2 and 2.4.1.3 (Öztürk, 2005).
Figure 2.4.1.1 Basic approach of Debris recycling operation (Öztürk, 2005)
Figure 2.4.1.2 Combined approach of Debris recycling operation (Öztürk, 2005)
Figure 2.4.1.3 Approach of Debris recycling operation with using recycling machines
(Öztürk, 2005)
Recycling operation starts classification of the materials process. Before planning and
classification of materials, economical evaluation should be done considering labor and
Debris Manual Separation Recycled materials
Final Disposal Areas
Debris Screening Recycled materials
Final Disposal Areas
Separation at
the band
Debris Crushing Recycled materials
Final Disposal Areas
Mechanical
Separation
17
transportation costs (Öztürk, 2005). Recycling machines which are used for urban
renewal projects in İstanbul are seen in Figure 2.4.1.4. Recycling process starts with
screening process, separation of soil and aggregate, that the final product should be
smaller than 38 mm. If the final product’s specifications are not between limits, it is sent
to the final disposal area. Big size rubbles are crushed mechanically so that iron scrap is
separated by using a magnetic band and also different size of aggregates are separated
by screening process. At the recycling facility in Istanbul (İSTAÇ) the aggregate size
fall within the range 0 mm – 38 mm.
Figure 2.4.1.4 Recycling machines are used at facility in Istanbul (İSTAÇ)
Scientific studies have revealed that recycled aggregate is suitable to use at places
where seismic load and physical effects are less. 0-12 mm aggregate is suitable to be
used as backfill concrete of pipelines. 12-22 mm aggregate is recommended to be used
as light path and pavement filler, while 13-22 and 23-38 mm aggregates are suitable to
use in backfilling of building and retaining wall and as drainage channel and backfill
material (İSTAÇ).
3. PROBLEM DEFINITION AND SOLUTION APPROACH
Due to the scarcity of relevant data, and considering the enormous number of the houses
in the disaster zone it is needed to be prepared for the impact of disaster since it is not
possible estimating time and size of disaster. In the view of the fact that it is not
possible to forecast the time and magnitude of the impending disaster, it is imperative to
take due precautions to counter its adverse effects.
screening machine Crushing and
screening machine
18
Considering the literature review part, there is a lack of scientific studies for debris
removal process in Turkey. In this thesis, the vehicle assignment problem was studied
for debris removal operation.
3.1. Solution Approach
Multi-objective mathematical programming is considered as the simultaneous
realization of multiple objectives in a mathematical programming structure. There are
many reasons of increasing interest in multi-purpose mathematical programming. The
first and most important one is that nature of many decision problems has multi
objective functions such as a debris removal operation aims to minimize costs of
operations/decisions, on the contrary aims to maximize amount of recycled material.
The other reason why the multi objective models have importance is that most of
production planning problems must meet standards like ISO 9001, TS16949, etc. The
last reason is ease and speed of computing solutions is ensured to solve the
multipurpose problem. In particular, it has reflected the developments in computer
problem solving (Atlas, 2008).
When existing literature is investigated, numerous methods are available to combine
objective functions of multi objective models such as multi objective linear
programming, goal programming, fuzzy theory, weighting technique, hierarchical
separation technique, normalization etc. In this study, Linear Physical Programming
(LPP) is used to solve the proposed model. LPP method uses crisp numbers, on the
other hand objective functions are piecewise linear which makes allowance to obtain
desirability levels of decision makers. In LPP, the designer does not need to decide the
weights of the objective functions in the problem formulation phase. On the contrary,
the designer need to specify ranges of different levels of desirability for each objective
functions. LPP provides a flexible and more deterministic approach to obtain a solution.
LPP explain criteria with using four different class types by declaring that each belong
to one of the classes. A criterion of a class is desired to be determined at two situations
as hard and soft. Figure 3.1.1 depicts the qualitative and quantitative meanings of each
soft class. The value of criterion under consideration, OFg, is shown on the horizontal
axis, and the function that will ve minimized for that criterion, zi, is shown on the
vertical axis. The preference ranges are (Maria, et al., 2003; Gulsun et al., 2009):
19
Ideal range OFg ≤ tg1
Desirable range tg1 ≤ OFg ≤ tg2
Tolerable range tg2 ≤ OFg ≤ tg3
Undesirable range tg3 ≤ OFg ≤ tg4
Highly Undesirable range tg4 ≤ OFg ≤ tg5
Unacceptable range OFg ≤ tg5
The parameters tg1 through tg5 are physically meaningful constant that generate from
designer (Maria, et al., 2003; Gulsun et al., 2009).
For Class 1S, Maria et al. (2003) additional comments: “Consider the first curve of the
Figure 3.1.1, when the value of OFg is less than t+
g1, the value of the class function is
small and requires little further minimization. On the other hand, when the value of OFg
is between t+
g4 and t+
g5, the value of the class function is large and requires significant
minimization.”.
Most important properties of the class functions are:
i. Nonnegative, continuous, piecewise linear and convex
ii. zg at a given target level is the same for all class types.
LPP determines the weights (ŵ+
gs and ŵ-gs see Eq. (1)) which represent the incremental
slope of the class functions, zg. Negative and positive deviations of the objective value
OFg are represented as d-gs and d
+gs (Maria, et al., 2003).
𝑀𝑖𝑛 𝐽 = ∑ ∑(�̌�𝑔𝑠− × 𝑑𝑔𝑠
− + �̌�𝑔𝑠+ × 𝑑𝑔𝑠
+ )
5
𝑠=1
𝐺
𝑔=1
(1)
Subject to
𝑂𝐹𝑔 − 𝑑𝑔𝑠+ ≤ 𝑡𝑔,𝑠−1
+ ; 𝑑𝑔𝑠+ ≥ 0 ; 𝑂𝐹𝑔 ≤ 𝑡𝑔5
+
(for classes 1S, 3S, 4S; g = 1,…,G; s = 2,…,5)
(2)
𝑂𝐹𝑔 − 𝑑𝑔𝑠− ≥ 𝑡𝑔,𝑠−1
− ; 𝑑𝑔𝑠− ≥ 0 ; 𝑂𝐹𝑔 ≥ 𝑡𝑔5
−
(for classes 2S, 3S, 4S; g = 1,…,G; s = 2,…,5)
(3)
Eq. (1) shows the minimization of weighted deviations of the objective functions. Eq.
(2) applies the criteria belonging to all classes except Class 2S, on the other hand Eq.
(3) applies to criteria belonging to all classes except Class 1S (Maria, et al., 2003).
20
Figure 3.1.1. Class functions for linear physical programming (Maria et al., 2003)
Ž 3
Ž 4
Ž 5
Ž 2 Ž
3
Ž 4
Ž 5
DE
SI
RA
BL
E
TO
LE
RA
BL
E
UN
DE
SI
RA
BL
E
HI
GH
LY
UN
DE
S
UN
AC
CE
PT
AB
LE
UN
AC
CE
PT
AB
LE
HI
GH
LY
UN
DE
S
UN
DE
SI
RA
BL
E
TO
LE
RA
BL
E
DE
SI
RA
BL
E
Ž 2
Ž 3
Ž
4
Ž 5
UN
AC
CE
PT
AB
LE
HI
GH
LY
UN
DE
S
UN
DE
SI
RA
BL
E
TO
LE
RA
BL
E
DE
SI
RA
BL
E
ID
EA
L
Ž 3
Ž
4
Ž 5
Ž 2
DE
SI
RA
BL
E
UN
DE
SI
RA
BL
E
HI
GH
LY
UN
DE
S
UN
AC
CE
PT
AB
LE
TO
LE
RA
BL
E
ID
EA
L
Ž 3
Ž
4
Ž 5
Ž 2
Ž 3
Ž
4
Ž 5
DE
SI
RA
BL
E
TO
LE
RA
BL
E
UN
DE
SI
RA
BL
E
HI
GH
LY
UN
DE
S
UN
AC
CE
PT
AB
LE
UN
AC
CE
PT
AB
LE
HI
GH
LY
UN
DE
S
UN
DE
SI
RA
BL
E
TO
LE
RA
BL
E
DE
SI
RA
BL
E
ID
EA
L
t+
g1 t+
g2 t+
g3 t+
g4 t+
g5
t+
g1 t
+
g2 t+
g3 t+
g4 t+
g5 t
-
g5 t-
g4 t-
g3 t-
g2
t-
g5 t
-
g4 t-
g3 t-
g2 t-
g1
t+
g1 t
+
g2 t+
g3 t+
g4 t+
g5 t
-
g5 t
-
g4 t-
g3 t-
g2 t-
g1
OFg
OFg
OFg
OFg
zg
zg
zg
zg
CLASS 1S
CLASS 2S
CLASS 3S
CLASS 4S
1
3.2. General Structure and Formulation of Model
Debris removal operations have vital importance to reduce the effects on nature, human
and economy. Because of this situation the proposed model is designed considering
recycling amount of debris, cost of debris removal process, negative impact of it on
victims and emission index to calculate the effect of nature. One objective function
model is not enough to have realistic case and to get desired results.
Three objective functions model was considered for this case. First objective function
(OF1) minimizes the total cost of the vehicle assignment, collection, transportation,
recycling, demolishing processes etc. (see Eqs. (4)-(11)). It was emphasized in the
literature that the cost is negligible. For this case, time was considered as a cost.
The second objective function (OF2) minimizes the negative impact of amount of
disaster on the affected people (see Eq. (12)). It was aimed where population rate is
higher, debris should be removed there quickly.
The last objective function (OF3) minimizes the emission index (see Eqs. (13)-(17)).
During disaster time is most important one, on the other hand, it has importance while
the rate of climate changes increases.
In the proposed model, the main goal is assigning vehicles from vehicle location area to
the Disaster Affected Sites (DAS) and Temporary Storage Area (TSA) considering the
debris amount. Vehicle assignments are taken based on the amount of debris in the area
at the beginning of each semester. While heavily damaged buildings are destroyed
debris is transported from affected area i to temporary storage areas. These vehicles can
also be assigned to the temporary storage areas considering amount of the debris on the
places. After first period completed second period is started and debris is sent from
affected areas to temporary storage areas. After recycling operation, useless materials
are sent to disposal areas. The proposed model is shown on Figure 3.2.1.
The most imported point is that excavator is used for demolishing activity so is sent
based on heavily damaged buildings amount. On the other hand, loader and truck are
sent based on debris amount at disaster affected area. Loader is used to load debris on
truck so total loader’s capacities should be equal to total truck capacities. The other
point is recycling operation is done at only temporary storage areas.
2
Figure 3.2.1. Problem definition
Source of Vehicle
( j )
Private Public
X2jiet
X3jiet
X1jiet
Disaster affected area ( i )
Amount of
debris
(ait)
aa
i
The number of
heavily damaged
buildins
(a1it)
aa1
i
ymit
Temporary storage area ( k )
Amount of
debris (qkt
)
gdmkt
tmikikt
Z
iket
Disposal
area ( d )
tmkdkdt
Z1
kdet
tmikikt
tmididt
3
Definitions of index, variables and parameters of the proposed model are seen in
Appendix 8.
The objective functions of the model
Minimization of net total cost (OF1):
OF1 = OF11 + OF12 + OF13 + OF14 + OF15 + OF16 - OF17 (4)
𝑂𝐹11 = ∑(𝜑𝑘 × 𝜇𝑘)
𝐾
𝑘=1
(5)
𝑂𝐹12 = ∑ ∑ ∑(𝜑1𝑘 × 𝑡𝑚𝑖𝑘𝑖𝑘𝑡)
𝑇
𝑡=1
𝐾
𝑘=1
𝐼
𝑖=1
(6)
𝑂𝐹13 = ∑ ∑ ∑ ∑[(𝑋1𝑗𝑖𝑒𝑡 + 𝑋2𝑗𝑖𝑒𝑡 + 𝑋3𝑗𝑖𝑒𝑡) × (𝑅𝑗𝑒 + 𝑀𝑗𝑖 + 𝑑3𝑗𝑖 × 𝐵)]
𝑇
𝑡=1
𝐸
𝑒=1
𝐼
𝑖=1
𝐽
𝑗=1
+
∑ ∑ ∑ ∑[(𝑋4𝑗𝑘𝑒𝑡 + 𝑋5𝑗𝑘𝑒𝑡) × (𝑅𝑗𝑒 + 𝑀1𝑗𝑘 + 𝑑4𝑗𝑘 × 𝐵)]
𝑇
𝑡=1
𝐸
𝑒=1
𝐾
𝑘=1
𝐽
𝑗=1
(7)
𝑂𝐹14 = ∑ ∑ ∑ ∑ 𝑛1 × 𝑋1𝑗𝑖𝑒𝑡 × 𝑐1
𝑇
𝑡=1
𝐸
𝑒=1
𝐼
𝑖=1
𝐽
𝑗=1
(8)
𝑂𝐹15 = ∑ ∑ ∑ ∑(𝑛2 × 𝑐2 × 𝑋2𝑗𝑖𝑒𝑡)
𝑇
𝑡=1
𝐸
𝑒=1
𝐼
𝑖=1
𝐽
𝑗=1
+ ∑ ∑ ∑ ∑(𝑛2 × 𝑐2 × 𝑋4𝑗𝑘𝑒𝑡)
𝑇
𝑡=1
𝐸
𝑒=1
𝐾
𝑘=1
𝐽
𝑗=1
(9)
𝑂𝐹16 = ∑ ∑ ∑ ∑(𝑛3 × 𝑐3 × 𝑑2𝑖𝑘 × 𝑍𝑖𝑘𝑒𝑡)
𝑇
𝑡=1
𝐸
𝑒=1
𝐾
𝑘=1
𝐼
𝑖=1
+
∑ ∑ ∑ ∑(𝑛3 × 𝑐3 × 𝑑1𝑘𝑑 × 𝑍1𝑘𝑑𝑒𝑡)
𝑇
𝑡=1
𝐸
𝑒=1
𝐷
𝑑=1
𝐾
𝑘=1
(10)
𝑂𝐹17 = ∑ ∑ ∑ 𝐺𝑝 × 𝑔𝑑𝑝𝑚𝑘𝑝𝑡
𝑇
𝑡=1
𝑃
𝑝=1
𝐾
𝑘=1
(11)
The first objective function is the minimization of net total cost which is obtained by
subtracting income from total costs. Total costs are obtained as the summation of cost of
opening temporary storage area (OF11) which is calculated by multiplying the cost of
4
opening TSA and decision of opening TSA (5), cost of recycling debris at TSA (OF12)
which is calculated by multiplying the cost of recycling operations and amount of debris
transported from DAS to TSA (6), cost of allocation of vehicles from source of vehicles
o DAS (OF13) which is sum of multiplication of assigned vehicles amount and cost of
emission prefer, service and fuel (7), demolition cost (OF14) which is calculated by
multiplying the demolition cost, capacity of vehicles (is assumed equal for all vehicles
among each other) and amount of assigned excavator (8), loading cost (OF15) which is
calculated by multiplying loading cost, capacity of vehicles and amount of assigned
loader (9), cost of transporting vehicles from DAS to TSA and TSA to disposal area
(OF16) which is calculated by multiplying transportation cost, capacity of truck,
distances between locations and number of transported vehicles (10). Revenue of
recycled materials which is obtained from (OF17) multiplying sales cost and amount of
recycled materials (11), is assumed that purchaser is responsible for recycled materials
transportation.
Minimization of negative impacts (OF2):
𝑀𝑖𝑛 ∑ ∑((𝐴𝑖𝑡 + 𝐴1𝑖𝑡) × 𝑛𝑒𝑖 × 𝑛𝑖𝑟𝑎𝑡𝑒𝑡)
𝑇
𝑡=1
𝐼
𝑖=1
(12)
OF2 obtain multiplication of sum of debris (estimated amount of debris and number of
destroyed buildings), population ratio of DAS i and negative impact rate on i at period t
(12). The negative impact at TSA is ignored for the proposed model.
Minimization of Emission Rate (OF3):
Min OF31 + OF32 + OF33 (13)
𝑂𝐹31 = ∑ ∑ ∑ ∑[(𝑋1𝑗𝑖𝑒𝑡 + 𝑋2𝑗𝑖𝑒𝑡𝑋3𝑗𝑖𝑒𝑡) × 𝑑3𝑗𝑖 × 𝑒𝑑𝑒]
𝑇
𝑡=1
𝐸
𝑒=1
𝐼
𝑖=1
𝐽
𝑗=1
(14)
𝑂𝐹32 = ∑ ∑ ∑ ∑[(𝑋4𝑗𝑘𝑒𝑡 + 𝑋5𝑗𝑘𝑒𝑡) × 𝑑4𝑗𝑘 × 𝑒𝑑𝑒]
𝑇
𝑡=1
𝐸
𝑒=1
𝐾
𝑘=1
𝐽
𝑗=1
(15)
𝑂𝐹33 = ∑ ∑ ∑ ∑(𝑍𝑖𝑘𝑒𝑡 × 𝑑2𝑖𝑘 × 𝑒𝑑𝑒)
𝑇
𝑡=1
𝐸
𝑒=1
𝐾
𝑘=1
𝐼
𝑖=1
(16)
5
𝑂𝐹34 = ∑ ∑ ∑ ∑(𝑍1𝑘𝑑𝑒𝑡 × 𝑑1𝑘𝑑 × 𝑒𝑑𝑒)
𝑇
𝑡=1
𝐸
𝑒=1
𝐷
𝑑=1
𝐾
𝑘=1
(17)
OF3 is obtained by multiplying emission penalty of e emission indexes, number of
assigned vehicles and distances (14)-(17).
These three objective functions affect each other as follows:
i. If collection time of debris reduces, net total cost and emission penalty cost
would increases because of larger number of assigned vehicles at first period
instead of assigned through further time periods. As a result of this situation,
emission rate of vehicles might increase.
ii. If low emission index is preferred net total cost would increase because of
hiring cost of new model vehicles. For this model, fuel cost differences of
vehicles (new model consume less fuel) is ignored.
These three objective functions are combined by using LPP technique which is
explained at section 3.1 and equations (1)-(3).
Constraints:
∑ ∑ ∑ 𝑐2 × 𝑋2𝑗𝑖𝑒𝑡
𝑇
𝑡=1
𝐸
𝑒=1
𝐽
𝑗=1
≥ ∑ ∑ ∑ 𝑐3 × 𝑋3𝑗𝑖𝑒𝑡
𝑇
𝑡=1
𝐸
𝑒=1
𝐽
𝑗=1
(∀ 𝑖 = 1,2,3, … , 𝑛) (18)
∑ ∑ ∑ 𝑐2 × 𝑋4𝑗𝑘𝑒𝑡
𝑇
𝑡=1
𝐸
𝑒=1
𝐽
𝑗=1
≥ ∑ ∑ ∑ 𝑐3 × 𝑋5𝑗𝑘𝑒𝑡
𝑇
𝑡=1
𝐸
𝑒=1
𝐽
𝑗=1
(∀ 𝑘 = 1,2,3, … , 𝑛) (19)
∑ 𝑦𝑚𝑖𝑡
𝑇
𝑡=1
= 𝑎𝑎1𝑖 (∀ 𝑖 = 1,2,3, … , 𝑛) (20)
𝑦𝑚𝑖(𝑡+1) ≤ ∑ ∑ 𝐶1 × 𝑋1𝑗𝑖𝑒𝑡
𝐸
𝑒=1
𝐽
𝑗=1
(
∀ 𝑖 = 1,2,3, … , 𝑛 𝑎𝑛𝑑 ∀ 𝑡 = 1, … , 𝑛 − 1
) (21)
𝑦𝑚𝑖1 = 0 (∀ 𝑖 = 1,2,3, … , 𝑛 ) (22)
𝑡𝑚𝑖𝑘𝑖𝑘1 = 0 (∀𝑖 = 1, . , 𝑛; ∀𝑘 = 1, . , 𝑛) (23)
𝑡𝑚𝑘𝑑𝑘𝑑1 = 0 (∀ 𝑘 = 1, … , 𝑛; ∀ 𝑑 = 1, … , 𝑛) (24)
𝑔𝑑𝑚𝑘1 = 0 (∀ 𝑘 = 1,2,3, … , 𝑛) (25)
6
𝑄𝑘1 = 0 (∀ 𝑘 = 1,2,3, … , 𝑛) (26)
𝑎1𝑖(𝑡+1) = 𝑎1𝑖𝑡 − 𝑦𝑚𝑖(𝑡+1) (∀ 𝑖 = 1,2,3, … , 𝑛 𝑣𝑒 ∀ 𝑡 = 1, . . , 𝑛 − 1 ) (27)
𝑎𝑖1 = 𝑎𝑎𝑖 (∀ 𝑖 = 1,2,3, … , 𝑛) (28)
∑ 𝐶3 × 𝑍𝑖𝑘𝑒𝑡
𝐸
𝑒=1
≥ 𝑡𝑚𝑖𝑘𝑖𝑘(𝑡+1) (∀𝑖 = 1, . , 𝑛; ∀𝑘 = 1, . , 𝑛; ∀𝑡 = 1, . , 𝑛 − 1 ) (29)
∑ ∑ 𝑡𝑚𝑖𝑘𝑖𝑘𝑡
𝑇
𝑡=1
𝐾
𝑘=1
= 𝑎𝑎𝑖 + 𝑎𝑎1𝑖
(∀ 𝑖 = 1,2,3, … , 𝑛) (30)
𝑎𝑖(𝑡+1) = 𝑎𝑖𝑡 + 𝑦𝑚𝑖(𝑡+1) − ∑ 𝑡𝑚𝑖𝑘𝑖𝑘(𝑡+1)
𝐾
𝑘=1
(
∀𝑖 = 1, . , 𝑛; ∀𝑘 = 1, . , 𝑛;∀𝑡 = 1, . , 𝑛 − 1
) (31)
∑ 𝐶3 × 𝑍1𝑘𝑑𝑒𝑡
𝐸
𝑒=1
≥ 𝑡𝑚𝑘𝑑𝑘𝑑(𝑡+1) (
∀𝑘 = 1, . , 𝑛; ∀𝑑 = 1, . , 𝑛 𝑎𝑛𝑑 ∀𝑡 = 1, . , 𝑛 − 1
) (32)
𝑔𝑑𝑝𝑚𝑘𝑝𝑡 = ∑ ∑ 𝑡𝑚𝑖𝑘𝑖𝑘𝑡 × 𝛿𝑘𝑝
𝑃
𝑝=1
𝐼
𝑖=1
(
∀ 𝑘 = 1, … , 𝑛; ∀ 𝑝 = 1, … , 𝑛 𝑎𝑛𝑑 ∀𝑡 = 1, … , 𝑛
) (33)
∑ ∑ 𝑡𝑚𝑘𝑑𝑘𝑑𝑡
𝑇
𝑡=1
𝐷
𝑑=1
= ∑ ∑ 𝑡𝑚𝑖𝑘𝑖𝑘𝑡
𝑇
𝑡=1
𝐼
𝑖=1
− ∑ ∑ 𝑔𝑑𝑝𝑚𝑘𝑝𝑡
𝑇
𝑡=1
𝑃
𝑝=1
(∀ 𝑘 = 1, … , 𝑛) (34)
𝑄𝑘(𝑡+1) = 𝑄𝑘𝑡 + ∑ 𝑡𝑚𝑖𝑘𝑖𝑘𝑡 − ∑ 𝑔𝑑𝑝𝑚𝑘𝑝𝑡
𝑃
𝑝=1
𝐼
𝑖=1
− ∑ 𝑡𝑚𝑘𝑑𝑘𝑑𝑡
𝐷
𝑑=1
(
∀𝑘 = 1, . . , 𝑛; ∀𝑡 = 1, . , 𝑛 − 1
) (35)
𝑄𝑘𝑡 ≤ 𝑐𝑘𝑘 × 𝜇𝑘 (∀ 𝑘 = 1, … , 𝑛 𝑎𝑛𝑑 ∀𝑡 = 1, … , 𝑛) (36)
∑ 𝑡𝑚𝑖𝑘𝑖𝑘𝑡
𝐼
𝑖=1
≤ 𝑐𝑘𝑘 × 𝜇𝑘 (∀ 𝑘 = 1, … , 𝑛 𝑎𝑛𝑑 ∀𝑡 = 1, … , 𝑛) (37)
∑ 𝑍𝑖𝑘𝑒𝑡
𝐾
𝑘=1
+ ∑ 𝑍2𝑖𝑑𝑒𝑡
𝐷
𝑑=1
= ∑ 𝑋3𝑗𝑖𝑒𝑡
𝐽
𝑗=1
(
∀𝑖 = 1, … , 𝑛; ∀𝑒 = 1, … , 𝑛 𝑎𝑛𝑑 ∀𝑡 = 1, … , 𝑛
) (38)
∑ 𝑍1𝑘𝑑𝑒𝑡
𝐷
𝑑=1
= ∑ 𝑋5𝑗𝑘𝑒𝑡
𝐽
𝑗=1
(
∀𝑘 = 1, … , 𝑛; ∀𝑒 = 1, … , 𝑛 𝑎𝑛𝑑 ∀𝑡 = 1, … , 𝑛
) (39)
7
∑ 𝑋1𝑗𝑖𝑒𝑡
𝐼
𝑖=1
≤ 𝑓1𝑗𝑒
(∀𝑗 = 1,2, … , 𝑛; ∀𝑒 = 1,2, … , 𝑛 𝑣𝑒 ∀𝑡 = 1,2, . . , 𝑛) (40)
∑ 𝑋2𝑗𝑖𝑒𝑡
𝐼
𝑖=1
+ ∑ 𝑋4𝑗𝑘𝑒𝑡
𝐾
𝑘=1
≤ 𝑓2𝑗𝑒 (
∀𝑗 = 1,2, … , 𝑛; ∀𝑒 = 1,2, … , 𝑛 𝑎𝑛𝑑 ∀𝑡 = 1,2, . . , 𝑛
) (41)
∑ 𝑋3𝑗𝑖𝑒𝑡
𝐼
𝑖=1
+ ∑ 𝑋5𝑗𝑘𝑒𝑡
𝐾
𝑘=1
≤ 𝑓3𝑗𝑒 (
∀𝑗 = 1,2, … , 𝑛; ∀𝑒 = 1,2, … , 𝑛 𝑎𝑛𝑑 ∀𝑡 = 1,2, . . , 𝑛
) (42)
𝑋1𝑗𝑖𝑒𝑡, 𝑋2𝑗𝑖𝑒𝑡, 𝑋3𝑗𝑖𝑒𝑡 ≥ 0; Integer (∀𝑗 =, … , 𝑛; ∀𝑖 = 1, … , 𝑛;
∀𝑒 = 1, … , 𝑛 𝑎𝑛𝑑 ∀𝑡 = 1, . . , 𝑛 )
(43)
𝑋4𝑗𝑘𝑒𝑡, 𝑋5𝑗𝑘𝑒𝑡 ≥ 0; Integer (∀𝑗 =, … , 𝑛; ∀𝑘 = 1, … , 𝑛;
∀𝑒 = 1, … , 𝑛 𝑎𝑛𝑑 ∀𝑡 = 1, . . , 𝑛 )
(44)
𝑍𝑖𝑘𝑒𝑡, 𝑍1𝑘𝑑𝑒𝑡, 𝑍2𝑖𝑑𝑒𝑡 ≥ 0; Integer (∀𝑖 =, … , 𝑛; ∀𝑘 = 1, … , 𝑛; ∀𝑑 = 1, … , 𝑛;
∀𝑒 = 1, … , 𝑛 𝑎𝑛𝑑 ∀𝑡 = 1, . . , 𝑛 )
(45)
𝑡𝑚𝑖𝑘𝑖𝑘𝑡, 𝑡𝑚𝑖𝑑𝑖𝑑𝑡 , 𝑡𝑚𝑖𝑘𝑘𝑑𝑡 ≥ 0 (∀𝑖 = 1, … , 𝑛; ∀𝑘 = 1, … , 𝑛; ∀𝑑 = 1, … , 𝑛
𝑎𝑛𝑑 ∀𝑡 = 1, . . , 𝑛 ) (46)
𝜇𝑘 = (0,1) (∀𝑘 = 1,2, … , 𝑛) (47)
𝑄𝑘𝑡, 𝑔𝑑𝑝𝑚𝑘𝑝𝑡 ≥ 0 (∀𝑘 = 1, … , 𝑛; ∀𝑝 = 1, … , 𝑛
𝑎𝑛𝑑 ∀𝑡 = 1, . . , 𝑛 )
(48)
𝑎𝑖𝑡 , 𝑎1𝑖𝑡 ≥ 0 (∀𝑖 = 1,2, … , 𝑛); ∀𝑡 = 1,2, . . , 𝑛) (49)
Eqs (18)-(19) try to guarantee that total assigned loader capacity is enough to load
debris at total quantity of assigned trucks.
Eq (20) tries to guarantee that sum of demolished quantity of buildings for all time
period equal to number of destroyed buildings at each DAS.
Eq (21) tries to guarantee that total capacity of assigned vehicles enough to demolish
the destroyed buildings at each DAS.
Eqs (22)-(26) impose constraints on the amounts demolished buildings at DAS,
transported from DAS to TSA and TSA to disposal site, recycled and inventory at TSA
in the first time period.
8
Eq (27) is the balance constraint between demolished amount and number of destroyed
buildings at each DAS for each time period. The demolished amount is assumed as
debris amount at the next time period.
Eq (28) concerns inventory of debris at first time period.
Eq (29) tries to guarantee that total number of assigned trucks must be enough to
transport debris from DAS to TSA. It is assumed that transported amount of debris from
DAS will add the inventory of the TSA at the next time period.
Eq (30) tries to guarantee that total transported amount of debris from DAS is equal to
sum of initial amount of debris and numbered of destroyed buildings amounts.
Eq (31) is the balance constraint between demolished, transported amount and inventory
of debris at each DAS for each time period.
Eq (32) tries to guarantee that total number of assigned trucks must be enough to
transport debris from TSA to disposal sites. It is assumed that transported amount of
debris from TSA will add the inventory of the disposal site at the next time period.
Eq (33) defines the recycled amounts for the use where the ratio of amount of recycled
material to the transported amount of debrid from DAS to TSA.
Eq (34) tries to guarantee that total transported amount of debris from TSA to disposal
site is equal to sum of recycled amount of debris for each time period.
Eq (35) is the balance constraint at inventory of debris at each TSA for each time period
considering transported debris from DAS to TSA and TSA to disposal site and recycled
amount.
Eqs (36)-(37) try to guarantee that inventory at TSA and transported amount of debris
from DAS to TSA for each time period must not exceed the capacity of TSA.
Eqs (38)-(39) try to guarantee that total number of transported vehicles must equal to
total number of assigned trucks from source of vehicle j to DAS i or TSA k for each
time period.
9
Eqs (40)-(42) try to guarantee that number of assigned vehicles does not exceed the
number of vehicles at vehicles sources. It is assumed that all assigned vehicles come
back from DAS and TSA to source of vehicles at the beginning of each time period.
Eqs (43)-(45) try to guarantee that these decision variables are non-negative and integer.
Eq (46 tries to guarantee that transported amount decision variables are non-negative.
Eq (47) tries to guarantee that opening TSA decision variable is binary.
Eqs (48)-(49) try to guarantee that these decision variables are non-negative.
3.3. Modeling Challenges
In this thesis, some difficulties are encountered due to various reasons during the
modelling process of the debris removal problem. The encountered difficulties as are
summarized below:
The most important challenge encountered is that being a limited number of
establishments for debris recycling operation in Turkey. The used data on the
model were collected from İSTAÇ which is the biggest and experienced
establishments for this subject in Turkey.
Disaster management efforts made a few years in Turkey and there is
insufficient information and data in this regard. Even if some types of data are
accessed easily accessing previous data on this case was very difficult.
Arc and node routing problem is studied for debris removal problem and
recycling issue is not dealt with any of the paper. There have been difficulties in
finding similar researches. So it has become difficult to adapt international
examples to Turkey.
Determining weights of objective function were very hard due to the small
number of authorized persons can get suggestions to determine weights.
10
3.4. Estimation of Input Data
The proposed methodology is applied in numerical example for Sakarya Case.
Assumptions and acceptances of the model were determined using data of previous
disasters and the consideration of authorities’ suggestions and data were obtained from
the institutions working on this issue and articles.
Three objective functions are weighted according to the consideration of authorities’
suggestions. Weights of objective functions are shown on Table 3.4.1.
Table 3.4.1. Weights of objective functions
Weight
Total cost 0,65
Negative impact on victims 0,3
Emission index of vehicles 0,05
According to AFAD, 66.441 homes and 10.901 workplaces were heavily damaged,
67.242 homes and 9.927 workplaces were moderately damaged, 80.160 homes and
9.712 workplaces were slightly damaged by 1999 Marmara earthquake in sakarya
(Gökçe and Tetik, 2012). Data of demolished and heavily damaged buildings are
estimated with using 1999 Marmara earthquake data and the amount of homes from
Turkish Statistical Institute (TUİK) which is changed by considering new districts of
Sakarya such as Arifiye, Erenler, Serdivan. The used data for demolished, heavily
damaged buildings and 2015 population ratio of disaster affected places which is found
from internet are seen on Table 3.4.7. are seen in Table 3.4.2. The DASs , TSAs,
location of vehicles, disposal sites and their relations are displayed in Figure 3.4.1.
The data of vehicles’ locations are hypothesized based on the location of governmental
agencies and excavation companies at Sakarya. TSA (k) are hypothesized considering
empty fields. According to the information received from authorized people two
disposal areas (d) are used in the model. While distances between 16 districts of
Sakarya (i) and location of vehicles or temporary storage area, It is assumed that center
of the damage was the midpoint of the districts. The data of distances between locations
of vehicles and disaster affected areas (dji), temporary storage areas and disposal areas
(d1kd), disaster affected areas and temporary storage areas (d2ik), disaster affected areas
11
and disposal areas (d3id), locations of vehicles and temporary storage areas (d4jk) are
estimated with using Google Maps. The tables of the data of distances are seen in
Appendix 3,4,5,6.
Table 3.4.2. Quantity of demolished and heavily damaged buildings
Districts
Quantity of
demolished
buildings (aai)
Quantity of
damaged
buildings (aa1i)
Population Population
Rate
Pamukova i1 145,65 1141,6 28506 0,03
Taraklı i2 107,95 387,8 6991 0,01
Kocaali i3 546,2 1312,6 21050 0,02
Hendek i4 9,1 2756,2 78179 0,08
Geyve i5 811,5 1925,4 48374 0,05
Sapanca i6 3264,8 4897,2 39686 0,04
Söğütlü i7 6,1 622 13960 0,01
Akyazı i8 141,45 3348,4 85499 0,09
Kaynarca i9 50 400 23489 0,02
Ferizli i10 130 500 24834 0,03
Karapürçek i11 500 700 12381 0,01
Adapazarı i12 10000 18300 269079 0,28
Karasu i13 200 1300 59130 0,06
Arifiye i14 4200 3150 39632 0,04
Serdivan i15 7300 8250 120731 0,13
Erenler i16 4700 5245 81660 0,09
Total 32112,75 54236,2 953181 1
12
Figure 3.4.1. DASs , TSAs, location of vehicles, disposal sites and their relations
The vehicles capacity (c1, c2, c3) and cost (n1, n2, n3) of demolishing, loading and
transportation data are found on internet are assumed as standard for every type of
vehicles. The data of them is seen in Table 3.4.3.
The data of the quantity of vehicles (f1, f2, f3) are assumed for governmental agencies
and found on internet for excavation companies. The tables of the data of vehicle
quantities are seen in Table 3.4.4.
13
Table 3.4.3. Capacity of vehicles and cost of work
Type of
Vehicles
Capacity of Vehicles
(m3 x 66 days)
Cost of work
(TL x 66 days)
Excavator 62,04 10454
Loader 237,6 10454
Truck 1056 7920
Table 3.4.4. Quantity of excavator, loader and truck at location of vehicle j
QUANTITY EMISSION INDEX
OF EXCAVATOR
EMISSION INDEX
OF LOADER
EMISSION INDEX
OF TRUCK
VE
HIC
LE
LO
CA
TIO
N A
RE
A
e0 e1 e2 e3 e4 e0 e1 e2 e3 e4 e0 e1 e2 e3 e4
j1 0 2 3 0 2 0 4 5 4 2 0 9 0 6 0
j2 3 7 0 0 0 5 11 6 3 0 5 11 6 3 0
j3 4 7 0 2 0 9 17 6 3 0 10 24 11 5 0
j4 0 2 1 0 0 0 10 3 0 0 0 10 3 0 0
j5 11 14 5 0 0 15 21 7 5 2 19 24 12 10 0
j6 7 12 0 0 0 18 26 3 3 0 18 40 8 5 0
j7 7 4 0 0 0 10 110 10 0 0 10 10 10 0 0
j8 4 10 0 0 0 3 12 10 0 0 5 18 15 0 0
j9 2 2 0 0 0 5 5 15 0 0 8 2 15 0 0
j10 2 11 0 0 0 10 10 0 0 0 12 13 0 0 0
j11 7 3 4 0 0 5 15 5 0 0 5 19 6 0 0
j12 8 7 2 0 0 5 13 2 0 0 5 23 2 0 0
j13 8 5 0 0 0 20 15 0 0 0 22 18 0 0 0
j14 7 9 9 3 0 12 20 11 2 0 16 30 20 4 0
j15 7 8 5 0 0 10 20 10 0 0 14 24 12 0 0
j16 3 12 5 0 0 5 18 2 0 0 7 31 4 0 0
j17 4 10 7 0 0 4 11 5 0 0 6 16 8 0 0
j18 9 8 2 0 0 10 20 5 0 0 14 22 5 0 0
j19 0 5 2 1 1 0 1 2 1 2 0 11 8 12 1
j20 0 2 8 0 0 0 3 2 3 0 0 0 0 19 2
j21 0 6 2 0 0 0 2 2 0 0 0 5 8 4 0
One t period is assumed as three months. So the capacity of vehicles is assumed equal
and found by multiplying with 66 days. Fuel cost of vehicles (B) is assumed as 10560
TL/3 months is found calculating the average of the amount of fuel (20 TL/hour).
Capacity of temporary storage areas (ck) are assumed based on the maximum three
months (t period) production capacity of the recycling machines is 24000 m3/3 months.
14
The opening cost of temporary storage areas (𝜑) are assumed as 1774800 TL
considering to be bought two screening and a crushing machines for each one of them.
The data of emission penalty of e emission index (ed) is assumed based on a report
published by the truck manufacturers are given in the following Figure.3.4.1.
Figure 3.4.2. Penalty of e emission index
The sales prices of recycled materials (g) are assumed based on internet price for iron,
İSTAÇ data for aggregate. The sales prices of recycled materials are seen in Table 3.4.5.
Table 3.4.5. The sales prices of recycled materials
PRICE/m3 Iron
0-12 mm
aggregate
13-22 mm
aggregate
23-38 mm
aggregate
Price 600 1,5 2 2
The cost of recycling process (𝜑1) is assumed as 0,56 TL/m3 based on the information
received from İSTAÇ.
The recycling rates of debris are assumed based on the information of the average
amount of recycling debris received from İSTAÇ. It is seen in Table 3.4.6.
Euro 6
Euro 5 Euro 4
Euro 2
Euro 3
Euro 1
1 2 3 4 5 6 8 7 -95 %
-97
%
0,10
0,20
0,30
0,40
NOx (g/kWh)
PM (g/kWh)
ede Euro 1 1993 0,35
Euro 2 1996 0,15
Euro 3 2000 0,10
Euro 4 2006 0,05 Euro 5 2009 0,05
Euro 6 2014 0,02
15
Table 3.4.6. The recycling rates of debris
Iron 0-12 mm
aggregate
13-22 mm
aggregate
23-38 mm
aggregate
Rate of
products 0,15 0,12 0,31 0,02
The negative impact rate on disaster affected areas for every time period (nirate) is
assumed based on study of Hu and Sheu, 2013 as 150t.
Labor cost for governmental agencies is assumed based on Minimum Wages in Turkey
with effect from 01-01-2016 to 31-12-2016 as 1300 TL/a month. Labor cost of 3 month
time period is 3900 TL/3 months. Labor cost for excavation companies is assumed
considering cost of service, 1000 TL/a month, as 3900 + 3000 = 6900 TL/3 months.
3.4.1. Test data set
Because of the proposed input data set’s solution time, a small data set is used to test the
model. The test data set has 5 DASs, 2 source of vehicles, 2 TSAs, 2 disposal areas, 3
time periods, 2 process types, 2 emission index. The data of emission penalty of e
emission index (ed) is assumed as 0.05 and 0.35. The amount of debris, the numbers of
demolished buildings and population rates are shown in Table 3.4.1.1.
Table 3.4.1.1. The amount of debris, the numbers of demolished buildings and
population rates
Quantity of
demolished
buildings (aai)
Quantity of
damaged
buildings (aa1i)
Population Rate
(nei)
i1 146 1141 0.04
i2 108 387 0.01
i3 547 1312 0.014
i4 9 2756 0.016
i5 812 1925 0.02
The distances between locations are seen in Table 3.4.1.2.
16
Table 3.4.1.2. The distances between locations
i1 i2 i3 i4 i5 k1 k2
j1 75.5 15.4 30.4 20.4 33.2 12.3 32.5
j2 42.5 7.59 64.4 2.13 24.6 2.7 65.3
k1 44.1 17.3 34.3 7.3 66 x x
k2 2.3 15.4 5.4 65.4 12.4 x x
d1 x x x x x 7.3 31.4
d2 x x x x x 17.3 15.4
The number of vehicles at source of vehicle locations is seen in Table 3.4.1.3.
Table 3.4.1.3. Test set’s quantity of excavator, loader and truck at location of vehicle j
EMISSION INDEX OF
EXCAVATOR
EMISSION INDEX OF
LOADER
EMISSION INDEX OF
TRUCK
e0 e1 e0 e1 e0 e1
j1 10 12 10 15 10 15
j2 10 12000 10 15000 8 20000
The recycling rates of debris and their prices are assumed as 0.15; 600 TL iron and 0.12;
1.5 TL 0-22 mm aggregate. The vehicle usage cost Rje are assumed as 10 TL and 6 TL
for public agencies, 1000 TL and 600 TL for private agencies.
3.5. Results and Analysis
The proposed model is run using input data which is mentioned at section 3.4 for 23
hours but a solution could not be obtained because of the existence large number of
integer variables on the other hand a feasible solution is obtained which is seen at the
Lingo screen which is seen at figure 3.5.1. So a smaller data set which has 5 DASs, 2
source of vehicles, 2 TSAs, 2 disposal areas, 3 time periods, 2 process types, 2 emission
index has been decided to use in order to get a solution.
After determination of the preference ranges of the objective functions, weights are
determined by using LPP technique. For the LPP technique considering the individually
results of objective functions, the preference ranges are decided as in Table 3.5.1. LPP
17
weight algorithm is run by using data shown in Table 3.5.1. When weights are
normalized and show in Table 3.5.2.
Figure 3.5.1. Lingo screen of the proposed model by using input data
Table 3.5.1. The preference ranges of the case study
OF1
Class 1S (min.)
OF2
Class 1S (min.)
OF3
Class 1S (min.)
Ideal range < 1500000 < 35000 < 850
Desirable range 1500000 - 2500000 35000 - 55000 850 - 1200
Tolerable range 2500000 - 3500000 55000 - 75000 1200 - 1500
Undesirable range 3500000 - 4000000 75000 - 95000 1500 - 2500
Highly Undesirable range 4500000 - 5000000 95000 - 105000 2500 - 3000
Unacceptable range < 5000000 < 105000 <3000
Table 3.5.3. Normalized weight deviations of objectives
�̌�12+ �̌�13
+ �̌�14+ �̌�15
+
OF1 0.1 0.121 0.736 0.043
�̌�22+ �̌�23
+ �̌�24+ �̌�25
+
OF2 0.245 0.061 0.074 0.62
�̌�32+ �̌�33
+ �̌�34+ �̌�35
+
OF3 0.047 0.025 0.025 0.903
18
The results of net total cost, the negative impact of the debris on affected people and
emission effect are obtained and seen in Table 3.5.4 when the proposed model is run by
using LPP technique.
Table 3.5.4. The numerical analysis
OF1 OF2 OF3
Numerical Result 1489019 35000 847.2020
The preference ranges Ideal range Ideal range Ideal range
Considering numerical analysis, all objective functions are in ideal ranges. As a result of
the LPP solution, number of assigned vehicles is shown in Table 3.5.5.
Table 3.5.5. Quantity of assigned excavator, loader and truck from location of
vehicle j to DAS i and TSA k
QUANTITY OF
EXCAVATOR
QUANTITY OF
LOADER
QUANTITY OF
TRUCK
j1 j2 j1 j2 j1 j2
i1 0 19 0 9 2 0
i2 3 4 0 5 0 1
i3 7 15 10 0 2 0
i4 0 45 0 14 0 3
i5 10 22 0 14 3 0
k1 x x 0 14 0 3
k2 x x 14 9 5 0
Total 20 105 24 65 12 7
Total
Vehicle
at j
22 12010 25 15010 25 20008
19
4. CONCLUSIONS
Disaster operation plan has a vital importance in reducing the effect of disaster on
human beings, natural environment, national economy and social structures. For the
disaster situation, the activities which reduce the negative impacts of disaster on
affected people, nature and economy as important as response and complete times of the
operations which are the most important factors. In this regard, debris removal
operations are becoming increasingly important.
In this thesis, vehicle allocation problem was handled considering the debris collection,
transportation and recycling operations. This model is a mixed integer programming
model. A model which has three objective functions as (i) minimization of operation
and decision net total costs, (ii) minimization of negative impacts of debris on people
and (iii) minimization of emission indexes of assigned vehicles is proposed for this
problem. LPP technique is used to integrate three objective functions into one objective
function. By employing this approach, typically complex texture of a decision maker’s
preferences can be satisfied. The weight of preference degrees for each performance
criteria is measured by using LPP technique which gives an advantage to remove the
essential to choose weights needed by some decision support tools. Lingo software is
used to run the proposed model. Because of the solution time of the proposed model’s
large data set, the smallest data set is used to obtain a solution. Considering numerical
analysis of test model, all objective functions are in ideal ranges.
Proposed methodology aims help the authorities, who work for this problem, in order to
conduct debris removal operations as quickly as possible considering total cost and
natural effects of debris and assigned vehicles.
For future research, firstly, Heuristic techniques such as Tabu Search, Genetic
Algorithms, simulating analyzing, etc. are proposed to run the proposed model for large
data set. Secondly, proposed model do not have decision of transportation of debris
from DAS to disposal site and it can be added so the proposed model might be
improved by adding the new criterion like maximum amount of recycled debris and new
constraints.
20
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APPENDIX
Appendix1: The classification of studies in disaster management and humanitarian logistics issues
Matematiksel Model
Author,
Date
Category
(Phase) of
Disaster
Topic of Study The objective functions Consideration of
Uncertainty Model Type Used Technique
Selection
Evacuatio
n Studies
Conceptional
Studies
Peeta et al.,
2010
Pre-
(Preparation)
Investment decisions to
strengthen the road
network
Expectations of the shortest path cost minimization Possibility of road
damage
Stochastic
programming 2-stage stochastic programming _ _
Görmez et
al., 2011
Pre-
(Preparation)
Facility location selection
(Location of storage
selection)
The first stage model:
The minimization of the distance which is weighted by
demand
The second stage model:
The first objective function:
The minimization of the average travel distance of victims
The second objective function:
minimization of the number of newly built facility
Scenario analysis
The first stage model:
Integer programming
The second stage
model:
Binary (0,1) Integer
programming
ε- constraint method _ _
Noyan, 2012 Pre-
(Preparation)
Determination the facility
location and the level of
inventory
The first stage model:
The cost minimization
The second stage model:
The cost minimization
The level of destruction in
demand and transport
network
Stochastic
programming
Two stage average-risk stochastic
programming _ _
Özgüven
and Özbay,
2013
Pre-
(Preparation)
Determination of
inventory level of
emergency needs
The cost minimization Inventory levels, demand Stochastic inventory
control model
p-level effective points (pLEPs)
method + Prѐkopa-Vizvari- Badics
algorithm
_
Usage of
RFID
technology
Salman and
Yücel, 2014
Pre-
(Preparation)
Facility location selection
(state of network
connection error)
Maximization of demand levels are met probabilities of different
scenarios occurrence
Stochastic integer
programming
Tabu search algorithm _ _
Kılcı et al.,
2015
Pre-
(Preparation)
Determination the
location of shelter
Maximization of the weight of the smallest weighted
shelter space
scenario analysis for
different parameter values
Mixed integer linear
programming Robust optimization _ _
Akgün et al.,
2015
Pre-
(Preparation) Facility location selection
Minimizing the risk (p-centered risk model);
Minimizing the maximum distance between the demand
point and the closest facility with it (p-centered model)
Fault decision tree
analysis for risks of
demand; scenario analysis
for different p values
Linearized integer
model;
p-centered risk model
(for comparison)
Fault tree analysis (for measuring the
resistance of demand points);
Solving methodology as linearization
and a linear integer program
_ _
26
Appendix1(Continued): The classification of studies in disaster management and humanitarian logistics issues
Matematiksel Model
Author, Date
Category
(Phase) of
Disaster
Topic of Study The objective functions Consideration of
Uncertainty Model Type Used Technique
Selection
Evacuatio
n Studies
Concep
tional
Studies
Üstün and
Anagün, 2015
Pre-
(Preparation) Mitigation budget allocation
The first objective function:
Maximizing the NPV of financial earnings from
mitigation investments
The Second objective function:
Maximization of the number of the
strengthening buildings
The third objective function:
Maximizing the investment of strengthen
certain strategically
important buildings and regions
_ Linear models;
Mixed integer models
Weighted sum method (Linear model);
Epsilon constraint method (Mixed integer
models);
Data envelopment analysis (for comparison of
Pareto efficient solution )
_ _
Barbarosoğlu
et al., 2002
After
(Response)
Top-level decisions:
Identifying the helicopter
fleet, the pilot assignments
and determination the
number of rounds
Lower level decisions:
routing and loading analysis
Top-level decision model:
Minimizing the cost of helicopters and pilots
Lower level decisions model:
Minimizing the service completion time
_
Top-level decision
model:
Integer programming
Lower level
decisions model:
Mixed Integer
Programming
Heuristic approach for coordination of
upper and lower level
multiple-
criteria
decision
analysis to
compare
alternative
solution
_
Barbarosoğlu
and Arda,
2004
After
(Response)
Transport situation in the
event of disaster response
The first stage model:
Minimization of total first stage transportation
costs and the costs of the expected relief
supplies
The second stage model:
Minimization of penalties costs associated with
the total flow, changing modes, holding
inventory and lack of inventory
uncertainty caused by the
damage to the transportation
systems are considered with
improved scenario analysis for
the supply parameters
Multi-product and
multi-modal network
flow model:
stochastic linear
programming
Stochastic linear programming approach _ _
Yi and
Özdamar,
2007
After
(Response)
logistics coordination model
for support and evacuation Minimization of service delays
Scenario analysis for Different
nodes, location and number of
vehicles
Mixed integer and
multi-product
network flow model
The first stage model:
Solution of mixed integer multi-product model
The second stage model:
Developing the vehicle routes and loading /
unloading instructions
_ _
27
Appendix1(Continued): The classification of studies in disaster management and humanitarian logistics issues
Matematiksel Model
Author, Date
Category
(Phase) of
Disaster
Topic of Study The objective functions Consideration of Uncertainty Model Type Used Technique
Selection
Evacuation
Studies
Concep
tional
Studies
Arşık and
Salman, 2013
After
(Response)
Modelling the
vulnerability of the
road network after an
earthquake
Route-based accessibility criteria Examined the possibility of
remain networks unclosed
Modelling the probability of
remaining durable the access roads
within the network
Statistical analysis _ _
Salman and
Gül, 2014
After
(Response)
Capacity allocation,
distribution emergency
needs and
providing medical
assistance service
Mixed integer model:
Minimizing the total time of transportation of relief supplies
and the total waiting time
Transportation and selection of location model:
Minimizing the costs of total emergency need's
transportation, total waited time and opening the field
hospital
scenario analysis for different
situations of parameters such os
patients arrival, number of
periods and transportation time
Mixed integer models (Dynamic
model of needs transportation)
+
Integer models
Hierarchical analysis
approach _ _
Aksu and
Ozdamar,
2014
After
(Response)
Determination of closed
roads and clearing them
with limited resources
(accessibility and
Evacuation)
The first stage model:
Maximization of the weighted earliest completion time for
the restoration of the route
The second stage model:
Maximization of the total early services for all regions in the
disaster areas
Modified the second stage model:
Minimization of the maximum difference between the two
early values of any region
Equipment availability analysis
for different scenarios
Integer programming (debris
removal scheduling model);
0-1 integer programming model
(equipment allocation model);
Modified integer programming
model (equipment allocation
model)
Integer programming _ _
Özdamar et
al., 2014
After
(Response)
analysis of existing and
potential residential
area
The first objective function:
Minimization of cumulative scale of
the failure to reach situation
The second objective function:
Minimization of completion time
Scenario analysis based on the
number of closure rate of
different roads and different
cleaning equipment
Iterative mixed integer modeling Heuristic _ _
Sahin et al.,
2015
After
(Response)
Debris removal during
disaster response period
Minimization of the total travel effort (transportation and
debris removal) were spent to clean the debris from closed
roads
Reducing solution time by
increasing the size of the
network increases
Arc and node routing (general
routing) model Heuristic _ _
28
Appendix 1(Continued): The classification of studies in disaster management and humanitarian logistics issues
Matematiksel Model
Author, Date
Category
(Phase) of
Disaster
Topic of Study The objective functions Consideration
of Uncertainty Model Type Used Technique Selection Evacuation Studies
Concep
tional
Studies
Onan et al.,
2015
After
(Recovery)
Determining the
location of the
temporary storage
center with the model
which include plans
of collecting and
transportation of waste
in order to find
environmentally
sustainable way
The first stage model:
The model for determining the location of temporary storage
centers
The first objective function:
Minimization of total weighted average distance to the point
source of waste in temporary storage
The second objective function:
minimization of the total population of cells including
temporary storage area
The second stage model:
Location determination and allocation model
The first objective function:
Minimizing the cost of opening the temporary storage area
and waste transportation for the temporary storage
The second objective function:
Minimization of population who exposed to the risk posed by
recycling and sorting plant
_ Multi-objective integer
programming model
2-stage multi-objective
optimization (NSGA-II) _ _
Alparslan et
al., 2008
Pre-
(Preparatio
n)
A geographic
information system
model for residential
suitability in order to
reduce the impact of
disasters
_ _ _ _
GIS model (distance from the
main benefit, ground
acceleration, geological soil type
and the slope of the land ):
to be investigated alternative of
existing settlements and new
settlements neighborhood of Bolu
in terms of earthquake resistance
_
29
Appendix 2: The Conceptional Studies
Author,
Date
Category
(Phase) of
Disaster
Conceptional Studies
Börühan et
al., 2012
Pre-
(Preparation)
The importance of management of logistics planning and
checklist for disaster management
Caymaz et
al., 2013
Pre-
(Preparation) Disaster crisis management
Ersoy ve
Börühan,
2013
Pre-
(Preparation) The importance of disaster logistics in terms of logistics
processes
Tanyaş et
al., 2014
Pre-
(Preparation) New Model for Disaster Logistics Management at Rize, Turkey
Kaynak and
Tuğer, 2014
Pre-
(Preparation)
Coordination and collaboration functions of disaster
coordination centers for humanitarian logistics
Jahre et al.,,
2015
Pre-
(Preparation)
Determining the needs of the supply chain by examining the
example of 3 different earthquakes in the past
Güzey, 2015
Pre-
(Preparation)
The earthquake risk of the area at risk for Disaster and urban
development and urban renewal policies in Ankara were
investigated taking into consideration the recent legislation
concerning the area at risk for Disaster.
Ozkazanc ve
Yuksel,
2015
Pre-
(Preparation)
Evaluation of disaster awareness and sensitivity levels of tertiary
students were examined. Date for this project was obtained with
questionnaire data collection methods from the students who
study at Gazi University Faculty of Architecture, Urban and
Regional Planning program. The need to reduce disaster losses
in education have been revealed with this Project.
Koçak vd.,
2015
Pre-
(Preparation)
Against disasters, preparations of individual behavior of
emergency medical services personnel are determined. In the
study, Mann-Whitney and Kruskal-Wallis and chi-square
statistical techniques were used. In conclusion, no matter at what
level of education employees have, It has been decided that they
should receive training for disasters and emergencies.
Albayrak
vd., 2015
Pre-
(Preparation)
In this study, Rapid seismic risk assessment was conducted for
the existing building stock in urban areas. Proposed
methodology for evaluation of seismic failure risk in urban
buildings' stock was developed by SUCUOĞLU is based on the
screening procedure technique. Age of the building, the number
of disasters, the presence of small incident, short column, heavy
setback and pounding effect was used for risk assessment.
30
Appendix 3: Distances between vehicle location area j to disaster affected area i
DISTANCE (km)
AFFECTED AREA
i1 i2 i3 i4 i5 i6 i7 i8 i9 i10 i11 i12 i13 i14 i15 i16
VE
HIC
LE
LO
CA
TIO
N A
RE
A
j1 42,5 64,4 73 35 32,4 17,6 22,3 30,8 33,9 26,7 24,5 8,8 55,7 10,7 7 4,3
j2 43,5 65,4 75,1 37,5 35,2 16,1 24,4 33,3 34,8 28,8 27 10,8 57,8 11,7 5,6 6,9
j3 45,8 67,7 73,7 40,2 37,5 18,8 23 36,1 33,3 27,4 29,8 9,4 56,4 14 4,7 8,2
j4 45,3 67,3 71,5 37,2 37,1 19,5 28,8 33 31,3 25,2 26,8 7,2 54,2 13,5 5,5 6,6
j5 43,2 65,2 70 35,3 35 19,6 19,3 31,2 33,3 23,6 24,9 7 52,6 11,4 9 4,6
j6 43 64,9 71,9 35 34,7 19,5 21,2 30,9 33,5 25,6 24,6 7,2 54,6 11,2 8,5 4,7
j7 40,1 62 74,2 31,9 31,8 16,6 23,5 27,7 40,3 27,9 21,4 14 56,9 8,3 8,8 1,6
j8 47,8 0,18 137 94,7 33,6 62 86,5 85,4 99,5 90,9 88,3 74 120 56,5 70,4 65,1
j9 53,5 75,4 72,8 45,5 45,2 27,6 21,3 41,3 23,6 26,5 34,9 13,2 55,5 21,7 13,7 14,7
j10 40,1 62 74,6 34,3 31,8 16,7 23,9 30,1 37,1 28,3 23,8 11,9 57,3 8,3 5,4 3,6
j11 0,26 47,1 114 71,5 14,2 38,9 63,1 62,2 76,4 67,5 65,2 50,9 96,5 33,3 47,2 42,1
j12 72,4 94,3 47,7 0,35 60,6 45,1 47,1 22,7 63,9 51,5 32,4 37,6 80,5 37 35,8 30,7
j13 66,2 88,1 53,2 5,5 57,9 46,3 50,4 23,1 67,2 54,8 28,3 40,9 83,8 34,4 37,7 34
j14 61,9 83,8 94,4 23,9 53,6 41,7 43,6 0,7 60,4 48 10 34,1 77 29,2 32,4 27,3
j15 41,2 63,1 75,2 28,9 32,9 17,5 24,5 24,7 41,2 28,8 18,5 14,9 57,8 9,4 8,2 3,5
j16 96,2 118 17,5 80,4 88 72,5 34,1 76,3 41,7 29,9 74,5 44,6 0,28 64,4 59,2 55,2
j17 46,4 68,3 84,7 40,4 38,2 18,3 29,9 36,2 40,3 34,3 30 16,4 67,4 14,6 11,1 12,6
j18 47,4 69,4 79,2 41,4 39,2 19,4 28,5 37,3 38,9 32,9 31 15 61,9 15,6 7,8 13,6
j19 42,8 64,8 72,9 37 34,6 17,8 22,2 32,9 33,1 26,6 26,6 8,6 55,6 11 5,6 11,6
j20 43,5 65,4 70 35,3 35,2 25 19,3 33,5 32,9 23,7 27,1 6,6 52,7 11,7 8,3 12,1
j21 43 64,9 72 35,1 34,8 19,6 21,3 30,9 33,4 25,7 24,6 7,1 54,7 11,2 8,3 9,7
31
Appendix 4: Distances between vehicle location area j to temporary storage area k
DISTANCE (km) DISPOSAL AREA
d1 d2
TE
MP
OR
AR
Y
ST
OR
AG
E
AR
EA
k1 17,3 11,4
k2 11,9 18,9
k3 17,6 21
k4 14,7 18,9
Appendix 5: Distances between disaster affected area i to temporary storage area k and
disposal area d
DISTANCE
(km)
TEMPORARY STORAGE AREA DISPOSAL AREA
k1 k2 k3 k4 d1 d2
AF
FE
CT
ED
AR
EA
i1 44,1 38,7 44,4 41,6 31,1 57,1
i2 66 60,6 66,3 63,5 53,1 79
i3 72,8 76,2 78,4 79,8 87,4 61,7
i4 38,5 32,2 27,9 35,5 43,1 41,3
i5 35,8 30,4 36,1 33,3 24 50
i6 18,5 16,2 20,7 10,4 11,9 29,9
i7 22,1 25,5 27,7 29,1 36,7 10,2
i8 34,3 28 23,8 31,4 38,9 37,2
i9 32,5 42,3 44,4 40 49,2 29,1
i10 26,5 29,9 32,1 33,5 41,1 15,4
i11 29,5 21,8 19,1 25,1 32,6 35,4
i12 8,5 16 18,1 16,1 27,2 7,4
i13 55,5 58,9 61,1 62,5 70,1 44,4
i14 14,1 6,9 12,6 6,4 6,6 25,3
i15 4,6 13 17 10,8 20,5 15,9
i16 6,4 6,8 0,65 10,2 17,7 17,3
32
Appendix 6: Distances between vehicle location area j to temporary storage area k
DISTANCE (km) TEMPORARY STORAGE AREA
VE
HIC
LE
LO
CA
TIO
N A
RE
A
k1 k2 k3 k4
j1 2,7 8,4 10,5 8,7
j2 3,1 7,6 11,6 5,4
j3 1,6 9,1 13 6,8
j4 2,1 11,8 15,8 9,6
j5 2,8 8,9 11,1 9,5
j6 3,6 10,6 11,2 9,6
j7 4,7 5,5 7,6 6,3
j8 65,8 60,5 66,2 63,3
j9 9,4 19,2 20,8 17
j10 4 7,4 9,4 7,6
j11 44,5 39,1 44,8 42
j12 38,4 32,1 27,8 35,5
j13 39,1 34,4 28,5 37,8
j14 34,9 28,6 24,3 31,9
j15 12,7 5 3,4 8,3
j16 55,2 58,6 60,8 62,2
j17 8,5 11,2 15,7 7,7
j18 7,1 12,5 17 8,9
j19 1,4 8,5 16,1 7,4
j20 3,1 11,2 12,9 9,7
j21 3 8,7 14,9 9,2
33
Appendix 7: Quantity of excavator, loader and truck at location of vehicle j
QUANTITY EMISSION INDEX
OF EXCAVATOR
EMISSION INDEX
OF LOADER
EMISSION INDEX
OF TRUCK
VE
HIC
LE
LO
CA
TIO
N A
RE
A
e0 e1 e2 e3 e4 e0 e1 e2 e3 e4 e0 e1 e2 e3 e4
j1 0 2 3 0 2 0 4 5 4 2 0 9 0 6 0
j2 3 7 0 0 0 5 11 6 3 0 5 11 6 3 0
j3 4 7 0 2 0 9 17 6 3 0 10 24 11 5 0
j4 0 2 1 0 0 0 10 3 0 0 0 10 3 0 0
j5 11 14 5 0 0 15 21 7 5 2 19 24 12 10 0
j6 7 12 0 0 0 18 26 3 3 0 18 40 8 5 0
j7 7 4 0 0 0 10 11 10 0 0 10 10 10 0 0
j8 4 10 0 0 0 3 12 10 0 0 5 18 15 0 0
j9 2 2 0 0 0 5 5 15 0 0 8 2 15 0 0
j10 2 11 0 0 0 10 10 0 0 0 12 13 0 0 0
j11 7 3 4 0 0 5 15 5 0 0 5 19 6 0 0
j12 8 7 2 0 0 5 13 2 0 0 5 23 2 0 0
j13 8 5 0 0 0 20 15 0 0 0 22 18 0 0 0
j14 7 9 9 3 0 12 20 11 2 0 16 30 20 4 0
j15 7 8 5 0 0 10 20 10 0 0 14 24 12 0 0
j16 3 12 5 0 0 5 18 2 0 0 7 31 4 0 0
j17 4 10 7 0 0 4 11 5 0 0 6 16 8 0 0
j18 9 8 2 0 0 10 20 5 0 0 14 22 5 0 0
j19 0 5 2 1 1 0 1 2 1 2 0 11 8 12 1
j20 0 2 8 0 0 0 3 2 3 0 0 0 0 19 2
j21 0 6 2 0 0 0 2 2 0 0 0 5 8 4 0
Appendix 8: Nomanclature
Index
Index Explanation
i
j
k
t
p
d
e
Disaster-affected area
Vehicle location
Temporary storage area
Time period
Process type
Disposal area
Emission index
34
Appendix 8-continue: Nomanclature
Variables
Index Explanation
𝑋1𝑗𝑖𝑒𝑡 The amount of excavator with e emission index is assigned from vehicle
location j to disaster affected area i at time period t
𝑋2𝑗𝑖𝑒𝑡 The amount of loader with e emission index is assigned from vehicle
location j to disaster affected area i at time period t
𝑋3𝑗𝑖𝑒𝑡 The amount of truck with e emission index is assigned from vehicle location
j to disaster affected area i at time period t
𝑋4𝑗𝑘𝑒𝑡 The amount of loader with e emission index is assigned from vehicle
location j to temporary storage area k at time period t
𝑋5𝑗𝑘𝑒𝑡 The amount of truck with e emission index is assigned from vehicle location
j to temporary storage area k at time period t
𝑍𝑖𝑘𝑒𝑡 The amount of truck with e emission index transport the debris from affected
area i to temporary storage area k at time period t
𝑍1𝑘𝑑𝑒𝑡 The amount of truck with e emission index transport the debris from
temporary storage area k to disposal area d at time period t
𝜇𝑘 Decision of opening temporary storage area k (0;1)
𝑄𝑘𝑡 The amount of debris in temporary storage area k at time period t
𝑔𝑑𝑝𝑚𝑘𝑝𝑡 The amount of recycled p type debris in temporary storage area k at time
period t
𝑎𝑖𝑡 The amount of debris remaining in disaster affected area i at time period t
𝑎1𝑖𝑡 The destruction amount remaining in disaster affected area i at time period t
𝑡𝑚𝑖𝑘𝑖𝑘𝑡 Debris transported from to disaster affected area i to temporary storage area
k at time period t
𝑡𝑚𝑘𝑑𝑘𝑑𝑡 Debris transported from to temporary storage area k to disposal area d at
time period t
35
Appendix 8-continue: Nomanclature
Parameters
Index Explanation
𝑚𝑗𝑖 The cost of assigning process of vehicles from vehicle location k to
affected area i
𝑚1𝑗𝑘 The cost of assigning process of vehicles from vehicle location k to
affected area i
𝑓1𝑗𝑒 The amount of excavator with e emission index at vehicle location j
𝑓2𝑗𝑒 The amount of loader with e emission index at vehicle location j
𝑓3𝑗𝑒 The amount of truck with e emission index at vehicle location j
𝑐1 Capacity of each excavator in the vehicle location
𝑐2 Capacity of each loader in the vehicle location
𝑐3 Capacity of each truck in the vehicle location
𝑐𝑘𝑘 Capacity of temporary storage area k
𝑑1𝑘𝑑 Distances between temporary storage area k and disposal area d
𝑑2𝑖𝑘 Distances between disaster affected area i and temporary storage area k
𝑑3𝑗𝑖 Distances between vehicle location j and disaster affected area i
𝑑4𝑗𝑘 Distances between vehicle location j and temporary storage area k
𝑎𝑎𝑖 The estimated amount of debris at disaster affected area i
𝑎𝑎1𝑖 The estimated amount to be demolition at disaster affected area i
𝛿𝑘𝑝 Debris ratio for process p which can be done at temporary storage area k
𝑔𝑝 income derived from process p
𝜑𝑘 Cost of opening temporary storage area k
𝜑1𝑘 Recycling processing cost at temporary storage area k
36
Appendix 8-continue: Nomanclature
Parameters
Index Explanation
𝑛1 Demolishing cost
𝑛2 Loading / unloading cost
𝑛3 Transportation costs
𝑛𝑒𝑖 Population ratio of i location
𝑛𝑖𝑟𝑎𝑡𝑒𝑡 Negative impact rate on i location at t time
𝑒𝑑𝑒 Emission penalty of e emission index
𝑅𝑗𝑒 Vehicle usage cost has to e emission index in j vehicle location
B Fuel costs
37
PERSONAL INFORMATION
Name and Surname: Lamia Gülnur KASAP
Place of Birth: Sakarya
Date of Birth: 15.05.1989
Address: Bağlar Mah. Yavuz Selim Cad. No:36 ökkuşağı Apt. aire:2 Erenler/Sakarya
GSM: 5333729390
Mail: [email protected]
EDUCATION
2013- :Marmara University, Industrial Engineering, M.S.
2011-2012 Fall Semester: Institute of Technology Tralee, Ireland Erasmus program
2008-2013: Sakarya University, Industrial Engineering, B.Sc.
2003-2007: Sakarya Figen Sakallıoğlu Anatolian High School
WORK INFO
11.07.11-05.08.11: Temsa Global / Adapazarı Factory – Work Study Internship
2011-2012 Spring Semester: Divan Furniture/ Kuzuluk Factory/ Mattress line – Project
Study
06.08.12-05.09.12: Kordsa Global Turkey/ İzmit/ Kocaeli – Management and
Production Internship
2012-2013: Sakarya University, Engineering Faculty, Department of Industrial
Engineering / Student assistantship
01.07.2013-03.02.2015: Sakarya İz Reklam Ltd. Şti/Arifiye/Sakarya- Quality Engineer
20.04.2015-Continue: Istanbul Medipol University , Engineering Faculty, Department
of Industrial Engineering / Research Assistant
38
PUBLICATIONS
Kasap L. G., Vayvay Ö., Tuzkaya G., (2015). Afet Lojistiği ve Türkiye’deki
Uygulamaları: Literatür Araştırması. IV. Ulusal Lojistik Ve Tedarik Zinciri Yönetimi
Kongresi, Gümüşhane, 1-10 (Loder Journal, January 2016)