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Naples waste crisisPolicy analysis report
14/12/2010
Group 7
Jonathan Aarnouts
Adrian Cebalos Lopez
Andrija Petrusic
Abraham Pedroza
Yingyao WangMarina Georgieva
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Table of contents
1. Introduction ............................. ........................ ................................ ...................... .......................... 2
2. Description of the causal relations in the system diagram ................................................. ............... 3
3. Alternatives ............................. ......................... ................................ ............................ .................... 4
4. Analysis of the alternatives ........................ ................................ ....................... ................................ 5
4.1 Impact table method ...................................................................................................................... 5
4.2 SMART table method ...................................................................................................................... 6
4.3 Results and suggestions .................................................................................................................. 7
5. Conclusions .............................. ........................ ................................ ...................... .......................... 7
Appendix A: System diagram and equations ........................................................................................... 10
Appendix B: Screening Alternatives ........................................................................................................ 15
Appendix C: Sensitivity analysis .............................................................................................................. 17Appendix D: Goal trees for public and private actor ............................................................................... 19
Appendix F: Extra reading materials ....................................................................................................... 20
References ............................................................................................................................................. 21
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1.IntroductionThe waste management crisis in Naples occurred due to a series of events leading to a waste collection
scarcity. Lack of incinerators, health risk, overfull and closed landfills are some of the reasons that
initiated this crisis. In addition to all this, the illegal waste dumping effectuated by the Italian mafia led to
a strike of the municipal waste collection workers that contributed to enhance and make worse the
Naples waste crisis which current situation degree can be seen with the waste piling up on the streets.
Determining and moreover suggesting which of various alternatives will be the most suitable, robust and
that will achieve a given set of goals through a descriptive and analytical analysis is the objective of this
policy analysis.
Knowing the government interests of keeping the people from the region satisfied by the action
performed without expanding the available budget is a challenging task. Not only is the dissatisfaction of
the citizens but also the bad impression towards the other countries in Europe politically at stake. Hence,how can the waste crisis rapidly and efficiently (in terms of costs and quality) be solved without affecting
the interests of the citizens (hygiene) and private companies (profits)?
In consideration that the system is not only influenced by the previous circumstances but also it is
influenced by several external factors such as garbage production, garbage disposed, etc. These external
factors are not always known beforehand, but can appear during the analysis or even during the
implementation of the solution, thus the system boundaries are considered in this report as well.
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2.Description of the causal relations in the system diagramThe main factor relating to the problem statement for the defined problem owner, namely the waste
commissioner, is the waste office budget since it reflects the causal relations in the system (Appendix A).
The available waste office budget is defined as the current available amount of money which can be used
to finance a solution for the crisis only affecting the Campagnia region. This budget is affected negatively
by the disposal, collection and recycling costs. Moreover, the waste office budget represents a factor
which is influencing the recycling, collection and disposal capacity which are actually the factors that
affect the total costs of waste management process.
As the waste commissioner is assigned by the government to solve the crisis within the available waste
office budget and is the responsible authority that represents the governments interest, he needs to
take care of how to keep the citizens from the region satisfied by the action performed regarding the
solution of the crisis. Waste commissioner has efficient waste management as his main goal objective.
High control of cost and efficient operational control can contribute to this. On one hand, for high controlof costs it is important to have low waste disposal cost and low waste collection costs. On the other hand,
efficient operational costs are defined by high waste disposal capacity, high waste collection capacity and
high waste recycling.
Taking into consideration the process of finding solution for the crisis and therefore the waste
management, the waste commissioner need to coordinate with the private companies, which are
representing another actor that influences the system. The interest and the wish of these private
companies is to maximize their profits. Due to the situation, some of the companies responsible for the
collection of the waste stopped operating. Furthermore, the lack of time to solve the crisis makes the
task for both types of companies more difficult to accomplish. Bigger profit from the contract is what theprivate companies have as their main goal objective. More efficient waste collection and higher income
contribute to this. More efficient waste collection is defined through bigger waste collection capacities
and lower operational costs, while higher income is defined through less penalties and more money for
collecting waste. The goal trees for both actors can be found in appendix D.
A main external factor that need to be taken into consideration and is influencing indirectly the system is
the Italian Mafia. They are affecting the amount of garbage dumped. The primary interest of the Italian
mafia is to continue with illegal dumping activities in order to make profit. In the current situation the
mafia is able to prevent the construction of new incinerators; any changes in this situation can have
negative consequences for them. However, the actions that can be used for reducing mafias activities are
not included in systems description.
Worth mentioning is the relation between the strikes against the government because of its inefficiency
in solving the crisis, money provided by the government and the waste office budget since it is not
immediately obvious. This relation depicts the situation in which more garbage dumped on the street
introduces bigger health risk for the citizens. The health risk for the workers involved in the process of
collecting, disposing and recycling the garbage is not taken into consideration. Therefore, the strikes that
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may be initiated by the workers because of their dissatisfaction caused by the exposure to hazards are
not included in the description of the system. The health risk for the citizens is expressed by the
registered disease cases caused by exposure to environmental hazards. Having to deal with an increased
health risk, the dissatisfaction of the citizens becomes higher. Therefore, there will be more unsatisfied
people who will express their revolt and dissatisfaction via strikes against the government. Having to deal
with more strikes, the government becomes more concerned about the problem. This situation
furthermore affects positively governments willingness to invest more money for solving the crisis,
which means that the waste office budget will be expanded (increased).
However, the government and so the waste commissioner doesnt want to increase the budget, but want
to solve the crisis with the budget available. In order to prevent this happening, the waste commissioner
has to do the job correctly and take the appropriate actions which will result in removed garbage, less
hazardous environment, less diseases and therefore more satisfied citizens who will gave up the idea of
striking against the government.
3.AlternativesDuring the brainstorm session a variety of solutions to the problem were defined (Appendix B), however,
in a policy analysis is not efficient to make a detailed assessment of all the proposals, therefore it is
necessary to make a screening of the alternatives to filter the more suitable solutions for the problem.
To make the screening is necessary to define broad criteria that are easy to identify in each alternative.
In the analysis the criteria considered are effectiveness, practicality, and cost of solutions (at a low level
of detail). A practical solution is related to the usefulness of the solution, this means that in addition to
be easily implemented, it is easy to continue with its use. The effectiveness is a criterion, since all the
proposed solutions help to improve the conditions of the problem, but some do to a lesser extent.
The list below represents the most suitable alternatives identified through applying the screening
methods on the list of possible alternatives that can be found in Appendix B.
1. Increase own disposal capacity The most efficient way of increasing own disposal
capacity is by combining the first and second policy solutions. These joint policies
enable an increase in disposal capacity as a long term solution.
2. Increase own collection capacity Temporary hiring working force and necessary
trucks during the crisis and constant growth of collection capacity due to population
growth will resolve the crisis and reduce the probability for future crisis.
3. Increasing disposal capacity by making new contracts This solution applies to
transfer the responsibility of disposing activities to a third party. This policy can cost
more than others, but it will be more efficient. The problem of this alternative is that
waste office needs to be aware of the mechanisms that a disposing process is
conducting by the third party, whit big emphasis on environmental issues.
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4. Increasing collection capacity by making new contracts This solution is similar to the
previous one; the difference is that a third party is hired for collecting waste but the
issues and worries of the waste office stay the same.
After selecting a small number of alternatives, a detailed analysis was made defining different criteria.
Those criteria are more quantitative and are focused on the approximate values that can be achievedwith the solutions or which can be a target value given by the actors. For the problem of garbage
collection in Naples, these criteria correspond to end user fees, the costs of the solution and capacities
for collection and disposal of the garbage.
Further, in the model there are some external factors that are difficult to control by the Waste
Commissioner, which in addition have a high uncertainty, so an evaluation of scenarios was made to
identify how it affected the different alternatives. In the analysis three scenarios regarding the Italian
mafia were identified: easy money, business-as-usual and risky business. The former scenario increases
the illegal dumping activities due to big profitability. The second scenario takes into consideration that
mafia continues the illegal activities in the same way. The latter scenario considers the situation in which
the crisis is solved by the government and the illegal dumping business becomes very risky due to the
increased control from the authorities.
The mafia activities are among the external factors that may have a greater effect in the solution, as
they impact the total cost of the solution as well as the capacities required for collection and disposal of
garbage. The easy money scenario requires more collection and disposal capacity, which leads to a
higher cost of the solution. The opposite happens in the risky business scenario.
.Analysis of the alternativesIn this chapter, we will analyze the four alternatives mentioned before by two main methods: impact
table and SMART table and some results and suggestions are given.
.1Impact table method
An impact table is a table in which each column corresponds to an alternative that is presented as a
possible solution. The rows represent the different criteria. The impact table can be used for decision
making by comparing the alternative solutions.
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Criteria A0 A1 A2 A3 A4
Fees(/HH/month) 5 6,68 7,14 6,36 7,47
Total Cost(M) 793 1.298 1.506 1.342 1.462
Collection capacity(Ton/day) 10.000 12.161 12.881 12.161 12.881
Disposal capacity(Ton/day) 7.000 18.600 12.881 12.161 18.600
Recycling capacity(Tons/day) 2.025 2.025 2.025 2.025 2.025
A0 Zero option (not implementing a solution)
A1 Increase own collection and disposal capacities
A2 Increase the allocation of new collection and disposal capacities by making new contracts
A3 Increase own collection capacity and allocation of new disposal capacity by making new
contracts
A4 Increase own disposal capacity and allocation of new collection capacity by making new
contracts
The values of the fees for the different alternatives are calculated under the assumption that the NPV of
the alternative is zero, and all the other basic assumptions are the same as in the alternative 0. In each
option, the costs of the implementation of the solutions are included and then the fee is determined in
order to have a neutral NPV. The calculations of such values are included in the excel file attached.
.2 SMART table method
SMART stands for Simple Multi Attribute Rating Technique. SMART is based on the impact table and
used to rank the different alternatives. SMART is however, more extensive than the scorecard model
since it uses weights to indicate the importance of each criterion and grades are given to the alternatives
to indicate the performance of this alternative for a particular criterion. Since the sums of the different
alternatives are relatively close to each other, a sensitivity analysis is performed to verify the robustness
of the alternatives. A detailed explanation of the sensitivity analysis and its results can be found in
appendix C. This appendix also elaborates on the assignment of the weights and the values for each
criterion.
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Criteria Weight A0 A1 A2 A3 A4
Collection capacity(Ton/day) 3 0,00 0,75 1,00 0,75 1,00
Disposal capacity(Ton/day) 3 0,00 1,00 0,75 0,63 1,00
Total Cost(M) 2 1,00 0,50 0,00 0,33 0,17
Fees(/HH/month) 1,5 1,00 0,40 0,20 0,60 0,00
Recycling capacity(Tons/day) 1 1,00 1,00 1,00 1,00 1,00
Weighted sum: 4,50 7,85 6,55 6,69 7,33
Rank order: 5 1 3 4 2
4.3Results and suggestions
The results of the impact table show the different alternatives with their corresponding impact on each
criterion. The problem owner can use this table to select the solution that will be implemented. The
impact table doesnt say which solution is the best or whether all actors will prefer a certain solution.
The SMART table aids the problem owner by indicating which solutions are the favorable in his/her point
of view.
This report provides the problem owner 4 suitable alternatives, using the previously mentioned tools.
However a specific solution cannot be suggested, since the problem owner is the one that needs to make
a decision based on his/her preference. It is not up to the analyst to determine the final solution.
However, the alternative A1 is the most robust one, because is not too expensive and it provides a good
solution for the waste crisis.
For recycling capacity in the impact table, we can see all four alternatives do not influence it, so besides
considering which alternative should be chosen, the problem owner should make other policy at the
same time in order to improve the recycling capacity, for instance increase the recycling rate and
publicize the benefits of recycling widely with big efforts.
5.ConclusionsThe Campania region in Italy currently has to deal with a waste crisis. The municipality struggles with
overfull landfills and illegal mafia activities. This has lead to severe health risk for the citizens and strikes
from municipal workers who are responsible for the collection and disposal of waste in Naples. In their
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efforts to solve the crisis, the government has appointed the waste commissioner to provide the citizens
with an efficient solution for the crisis, while not exceeding the available budget. Besides the fast
solution to the current situation, there are also measurements needed to prevent the crisis from
happening again in the future. Therefore the presented solutions both are aimed at solving on short
term the waste problem on the streets in the Campania region and on the long term by investing in the
total waste collection and disposal capacity.
In the process towards finding a solution, several policy analysis tools and techniques are used. These
tools and techniques helped in acquiring a profound understanding of the problem situation. The entire
situation is described in the system diagram. It contains all the actors with their respective goals and
wishes. These goals are translated into criteria that are used to assess possible solutions for the problem.
All possible solutions have been screened using two methods: an evaluation model and by using hard
constraints. The screening is needed to separate the wheat from the chaff. In other words, to reduce the
long list of possible solutions, to a short list with only the most suitable solutions. The four solutions or
alternatives that the most are suitable for the waste commissioner are: Increasing Campanias own
collection and disposal capacities (A1), increasing the allocation of new collection and disposal capacitiesof the Campania region by entering into new contracts with third parties (A2), increasing Campanias
own collection capacity and allocating new disposal capacity for the region by entering into new
contracts with external parties (A3), or increasing the disposal capacity of the Campania region and
allocate new collection capacity through contract agreements with third parties (A4). Next to the four
solutions there is also a zero-option of doing nothing. This option helps the problem owner to place the
alternatives in perspective.
The alternatives or solutions are also influenced by external factors such as the illegal mafia activities.
For each of the external factors, scenarios have been developed in order to determine their influence on
the proposed solutions under different circumstances. We identified three scenarios for the mafia: easymoney, business as usual and risky business that described an increased, unchanged or decreased level
of mafia activities.
Based on the screening and scenario analysis, we presented an overview of the scores of each
alternative for a certain criterion. This overview (also called the impact table) is an unbiased mean to
present the solution. The problem owner like any other actor- can use this table determine their best
solution. However, since this report is written upon instructions of the waste commissioner, we have
further analyzed the proposed solutions with the goals and wishes of this actor. The SMART table is
presents the outcome of this analysis. It shows that alternative one is the most robust and favorable
solution. This solution entails the hiring of new collection trucks and temporary employees to remove
the waste from the streets in the Campania region and dispose it on landfills and incinerators outside the
region. In the meantime, the foundation is laid out to prevent the crisis from happening again in the
future, by opening new landfills and constructing additional waste incinerators. A sensitivity analysis of
the different alternatives showed that this alternative is the most robust since it has a high ranking in
various weighting scenarios. This does not mean that this alternative is the cheapest solution nor that it
is the solution that will increase the collection and disposal capacity the most, but it does provide overall
the most beneficial solution. Finally, we need to remark that all four proposed alternatives do not
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influence the recycling capacity. Our analysis showed that the recycling capacity nevertheless is a very
important criterion. Therefore we advise that the proposed alternative one is complemented by
additional measurements that positively affect the total waste recycling capacity.
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Appendix A: System diagram and equations
Figure 1.1 System diagram
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The figure 1.1 represents a system diagram which is used to summarize the results of the policy
analysis of the waste crisis in Naples.
This diagram is made according to the precisely defined goal trees for the public and private actors
and the corresponding problem statements for both of them. This diagram reflects the factors,
goals and criteria that are found to be very important in the presented system. Moreover, it showsthe means that have been identified and how they influence certain factors.
All the factors represented in the diagram are listed below in the following table 1.1, together with
the corresponding units.
FACTORS UNITS
Citizens of Naples Household
Garbage production by citizens Ton/day
Average garbage production by a household Kg/day/Household
Dumped garbage TonGarbage disposed by the mafia Ton/day
Strikes against government inefficiency strikes/week
Waste office Budget Euro/year
Money provided by the government Euro/year
Collection costs Euro/Ton
Collection capacity Ton/day
Garbage processed Ton/day
Recycling capacity Ton/day
Recycling costs Euro/Ton
Disposal capacity Ton/day
Disposal costs Euro/Ton
Total costs Euro/year
Garbage Fees for citizens Euro/month/household
Registered disease cases because of exposure
to environmental hazards (pollution)
Sick people/month
Collected money from garbage fees Euro/Year
Table 1.1 Factors and corresponding units
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Taking into consideration the causal relations among the factors in the presented system diagram
and the table, the following equations are defined:
Disposal capacity(Ton/day)
+Waste office budget ()
T = Ey Wt-1 Ton/day = Ey E = Ton//day
Collection capacity(Ton/day)
+Waste office budget ()
N =^y Wt-1 ^ = Ton//day
Recycling capacity(Ton/day)+ Waste office budget ()
R = Ry Wt-1 R = Ton//day
Collection Cost (/Ton)
+Collection Capacity (Ton/day)
O = Oy A /Ton = Oy Ton/day O = No physical meaning of the dimensions
DisposalCost (/Ton)
+Disposal Capacity (Ton/day)
L = Oy P /Ton = Oy Ton/day O = No physical meaning of the dimensions
Recycling Cost (/Ton)
+Recycling Capacity (Ton/day)
I = Oy R /Ton = Oy Ton/day O = No physical meaning of the dimensions
Garbage processed (Ton/day)
+Collection Capacity (Ton/day)
+Disposal Capacity (Ton/day)
+Recycling Capacity (Ton/day)
B = Py MIN (A, P+R) P = dimensionless
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Fees (/month/household)
+Total costs (/Year)
F = Oy T O = Year/(month*household)
The factor O implicitly involves the number of households and the conversion of the units
from years to months. In the excel sheet, the fees are calculated assuming that the NPV
equals zero, in order to recover all the costs. If the waste office has an annual budget to
subsidize the collection and disposal of the garbage, the total cost T should be discounted in
the available budget.
This formula is not directly used because the fees and the total costs for each year have a
different discount rate. If the fee is calculated independently for each year, the formula could
be used to determine the correct fee that need to be charged to the households.
Total costs (/Year)
+Collection costs (/Year)+Disposal costs (/Year)
+Recycling costs (/Year)
T = Yy O + Ny L + Gy I Y = dimensionless N = dimensionless G = dimensionless
For each year, the total cost is calculated as the sum of the costs of collection, disposal and
recycling. In the excel sheet, the recycling was assumed as zero, because none of the
alternatives include the policy of encourage the recycling in the city, then the total cost for
each year is the sum of the collection and disposal costs as cab be seen in the rows Cash out
() in the excel sheets. For this particular case the coefficientsY, N and G are equal to 1.
Collected moneyfrom garbage fees(/Year)
+Citizens (Household)
+Fees (/household/month)
N = Yy C y F Y = month/Year
This formula is used in the excel sheet under the name Collection Fees () where the
Citizens C is calculated dividing the Total number of citizens measured in persons by the
number of persons per household. The coefficient Y is used to convert the units from months
to years and is equal to 12.
DumpedGarbage (Ton)
+Garbage production by citizens (Ton/day)
+Garbage disposed by mafia (Ton/day)
-Garbage Processed (Ton/day)
D = \y G + Sy M Vy B \ = day S = day V = day
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Garbage production bycitizens (Ton/day)
+Citizens (Household)
+ Average garbage production by a household (Kg/day/household)
G = Yy C y V Y = dimensionless
This formula is used in the excel sheet to calculate the amount of garbage produced in the
city per day. The factor Y is equal to 1, and the average garbage production by household V
takes into account the average number of persons per household.
Registered diseased people due to exposure to environmental hazards (sick people/ month)
+Dumped garbage (Ton)
E = Wy D W = sick people/month/ton
Strikes against government inefficiency(strikes/week)
+Registered diseased people due to exposure to environmental hazards (sick people/ month)
S = :y E : = No physical meaning of the dimensions
Moneyprovided bygovernment ()
+Strikes against government actions (strikes/week)
Y = Xy S X = /strikes/work
Waste office budget (/Year)
+Money provided by the government (/Year)
+Collected money from garbage fees (/Year)-Total costs (/Ton)
W = Yy Y + Ny N Gy T Y = TonN = TonG = Ton
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Appendix B: Screening Alternatives
There are two options for screening the different alternatives: using harsh constraints (cut-off
method) or using a simple evaluation model (cream off method). Good criteria are quantifiable and
make it possible to measure and compare the different tactics. The criteria for the this analysis are
Investment (Costs and Time) and feasibility (achievability). Since not all the alternatives emerged
from the brainstorming are achievable some criteria needs to be taken in order to determine which
alternatives are reachable and which ones are not. Three important facts for doing the latter are
effectiveness, practicality and cost because this classification of the alternatives is not a detailed
classification is more general. The final combination alternative should solve the crisis on short-term,
so with little investment time. Furthermore, the solution should also be with the budget that is
provided to the problem owner, so the new investment cant be too large. On long-term, you are
investing more money (and have the time available) to open landfills and build new incinerators. In
the end you should come up with a solution so that it is unlikely that the crisis will return (have a
large enough waste (collection and disposal capacity). Of course you should look for a solution thaton long term is feasible and does not harm the health of the citizens in the region.
Table B.1 and B.2 contain the results of the screening process.
No Alternative Practical Effective Cost Total
1Increase the number of incinerators (own disposal
capacity)8 10 6 24
2 Open new landfills (own disposal capacity) 8 9 4 21
3Temporary increase own collection capacity by hiring
hew workers and renting more trucks7 8 6 21
4 Hire new collection capacity8 9 4 21
5 Hire new disposal capacity 8 9 3 20
6 Start large recycling campaigns 7 6 6 19
7 Sending more waste abroad 6 8 4 18
8Implement a collecting system by garbage
classification5 8 5 18
9 Enlarge waste office budget 7 8 3 18
10
Investigate whether there have been similar
problems/situations (anywhere in the world) in the
past and copy their solution
6 5 6 17
11 Increase taxes during the crisis period5 5 7 17
12 Increase garbage collection fees in the whole region 4 5 8 17
13 Hire an external party to solve the problem 9 3 2 14
14 Eliminate illegal activities of the Mafia 4 5 3 12
15Differential fees according to the amount of
produced garbage per household2 4 6 12
16 Business as usual 1 1 10 12
Table B.1 Cream off screening method
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No Alternative Practical Effective Costs
1 Increase the number of incinerators (own disposal capacity) yes yes ++
13 Hire an external party to solve the problem yes yes ---
7 Sending more waste abroad yes yes -
2 Open new landfills (own disposal capacity) yes yes +
10
Investigate whether there have been similar
problems/situations (anywhere in the world) in the past and
copy their solution
yes no +
14 Eliminate illegal activities of the Mafia no no --
8 Implement a collecting system by garbage classification no yes 0
3Temporary increase own collection capacity by hiring hew
workers and renting more trucksyes yes +
6 Start large recycling campaigns yes no +
9 Enlarge waste office budget yes no --
15
Differential fees according to the amount of produced garbage
per household no no +
11 Increase taxes during the crisis period no no ++
12 Increase garbage collection fees in the whole region no no ++
5 Hire new disposal capacity yes yes +
4 Hire new collection capacity yes yes +
16 Business as usual no no +++
Table B.2 Cut off screening method
Below is a brief explanation of every remaining policy alternative and the expected policy impact
(what will be influenced / changed if this policy alternative is applied).
Increase own disposal capacity the most efficient way of increasing own disposal capacity is bycombining the first and second policy solutions. These joint policies enable an increase in disposal
capacity as a long term solution.
Increase own collection capacity Temporary hiring working force and necessary trucks during the
crisis and constant growth of collection capacity due to population growth will resolve the crisis and
reduce the probability for future crisis.
Increasing disposal capacity by making new contracts This solution applies to transfer the
responsibility of disposing activities to a third party. This policy can cost more than others, but it will
be more efficient. The problem of this alternative is that waste office needs to be aware of the
mechanisms that a disposing process is conducting by the third party, whit big emphasis on
environmental issues.Increasing collection capacity by making new contracts This solution is similar to the previous one;
the difference is that a third party is hired for collecting waste but the issues and worries of the
waste office stay the same.
The optimal solution is not only one of these policies, but a combination of 2 of them concerning the
collection and disposal capacity. According to the NPV table the best solution is the increase of own
disposal and collection capacities.
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Appendix C: Sensitivity analysis
Table C.1 Sensitivity analysis
Since the resulting values from the SMART table lie close to eachother, a minor difference in the
chosen weights could possibly lead to a completely different ranking outcome. To be able to
provide the a reliable and robust answer, a sensitivity analysis is performed. For the sensitivity
analysis, 5 different weighting scenarios were developed. Each colum represents a different
weighting scenario with their corresponding weights for each criterium. The different scenarios
result in different weighted sums and ranking of alternatives. The values of the weigths are
ranging from 0 (no value) to 3 (very important). The range of weights is small (max 3 diffence),
since in this way all criteria still have an influence on the alternatives. When the range is to large,
only the criteria with the highest weigths determine the final ranking of alternatives. The first
weighting scenario is based on the problem owners preference. The waste commisioners
(problem owner) interest lies in solving the waste crisis effectively and timely. Therefore, the
heighest weights are allocated to the collection and disposal capacity. Of course, theres is a
budget, but this is of less importance. The recycling capacity is seen as an addition critria for the
alternatives and has therefore assigned weight of 1. In the cost focus scenario, the criteria
regarding the total cost and waste fees receive the largest weigth. The recycling scenario focusses
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on the collection capacity and specifically on the recycling capacity. The final two scenarios assign
the most value to either the collection capacity or the disposal capacity.
The results from the scenario analysis show that the zero alternative (do nothing) is ranked the
lowest in nearly all scenarios except for the cost focus scenario, where it is the most favourable.
Furthermore, the analysis shows that in each weighting scenario, alternative 1 is ranked in the toptwo. Therefore, we can conclude that alternative 1 is the most robust and we advise the problem
owner to implement this alternative.
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Appendix D: Goal trees for public and private actor
Goal tree for public actor: Waste commissioner
Efficient WasteManagement
High control ofcosts
Low waste disposalcosts
[/day]
Low wastecollection costs
[/day ]
Efficientoperational control
High wastedisposal capacity
[T/day]
High wastecollection capacity
[T/day]
High waste recyling
[ T/day]
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Goal tree for private actor: Private companies
Appendix F: Extra reading materials
Bigger profit fromthe contract
More efficientwaste collection
Bigger waste
collection capacity
[T/day ]
Lower operational
cost
[/T]
Higher income
Less penalties[]
More money for
collecting waste
[/T]
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References
Truck rental per month: http://www.rdk.com/garbage_trucks_for_rent.htm
Capacity per truck : http://www.rdk.com/inventory_details.php?unit_id=0M0077#go
incinerator with processing capacities :
http://www.unep.or.jp/ietc/ESTdir/Pub/MSW/SP/SP5/SP5_2.asp
Population Campagnia region: http://en.wikipedia.org/wiki/Campania
Average salary + social contributions: http://www.worldsalaries.org/italy.shtml
Population increase: http://faculty.ed.umuc.edu/~jmatthew/naples/poobah.htm
Inflation: http://just4business.eu/2008/11/inflation-rate-in-europe-down/
Garbage per person: http://www.epa.gov/reg3wcmd/solidwastesummary.htm
Persons per household: http://campania.indettaglio.it/eng/comuni/na/gragnano/gragnano.html
Incinerator operating costs:
Prof. Dr.-Ing. Klaus GrnerWaste Incineration European State of the Art and New
DevelopmentsUniversityof Essen , Institute for Environmental Process Engineering and Plant
Design
Operational costs:
http://www.goodyear.eu/uk_en/sitewides/press/goodyearinthenews/2010/Goodyear_launches.js
p
http://science.howstuffworks.com/environmental/green-science/landfill4.htm
http://www.no-incinerator.org/questions/incineration-costs.html