Next Article in Journal
Support for Economic Inequality and Tax Evasion
Next Article in Special Issue
An Interpretative Matrix for an Adaptive Design Approach. Italian School Infrastructure: Safety and Social Restoration
Previous Article in Journal
Electricity Theft Detection Using Supervised Learning Techniques on Smart Meter Data
Previous Article in Special Issue
Enhancement of Small Towns in Inland Areas. A Novel Indicators Dataset to Evaluate Sustainable Plans
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Peripheralization Risk Mitigation: A Decision Support Model to Evaluate Urban Regeneration Programs Effectiveness

Department of Civil Engineering, University of Salerno, Via Giovanni Paolo II, 132-84084 Fisciano (SA), Italy
*
Authors to whom correspondence should be addressed.
Sustainability 2020, 12(19), 8024; https://doi.org/10.3390/su12198024
Submission received: 5 August 2020 / Revised: 24 September 2020 / Accepted: 25 September 2020 / Published: 28 September 2020

Abstract

:
The term peripheralization indicates a process that can generate social, physical, and environmental degradation in urban areas. In the light of the new urban geography and the socio-economic trends taking place globally, there is a risk that the typical decay of a peripheral condition may affect city in their entirety, regardless of spatial proximity to its centre. Then, regeneration interventions should be targeted primarily at areas with a significant peripheralization risk, understood as a combination of potential degradation factors. Consequently, the decision-makers’ choice of the best design alternative should be informed by the knowledge of pre-existing vulnerability levels, and oriented towards the solution that maximizes their reduction. This is possible when the planning of interventions in the most vulnerable areas, through Urban Regeneration Programs, is able to take into account the results of the project alternatives economic evaluation. Such an approach constitutes the main novelty of the study. So, the aim of the work is to provide a decision support model for the evaluation of urban regeneration interventions effectiveness in areas of high peripheralization risk. To this end, the contribution defines a set of mitigation indicators and the assessment of the most effective design alternative through analytic hierarchy process (AHP). The proposed model was applied to an area of Marcianise Municipality, in Campania Region (Italy).

1. Introduction

Since the 1990s, in developed countries, including Italy, there has been a phase of experimentation with tools to combat the degradation of urban areas supported by public funding, known as the season of ‘complex programmes’. On an urban scale, the latter are urban planning instruments implementing the general municipal plan, aimed at countering the physical and functional degradation of urban neighbourhoods, also facing social degradation. To this end, these programs provide for a plurality of project actions and involve multiple subjects, which is why they are called complexes [1].
Over the years, the European Commission has repeatedly funded urban decay reduction initiatives, from complex programmes to the latest urban regeneration programmes. Areas targeted by these programmes have often been urban peripheries, which in Europe and Italy, they are generally associated with degraded areas [2]. Nevertheless, as cities continue to grow worldwide, urban areas result in a series of challenges varying from natural resources consumption, or ‘spatial peripheralization’, to the development of social and economic imbalances and physical and environmental degradation, in a process of ‘a-spatial peripheralization’ [3,4,5,6,7,8,9,10]. Some aspects of such process can be assimilated to the topic of urban poverty [11] or to the deprivation issue, developed in the European context [12,13]. The issues of reducing land take and urban poverty, through regeneration of deprived areas, are central: In the most recent European Union recommendations [14,15] and in the New Urban Agenda, adopted by the United Nations on the basis of the 2030 Agenda for Sustainable Development, which recognizes urban planning as playing a key role in the definition and programming of mitigation actions [16].
The analysis of the main international experiences highlights how the regeneration of deprived areas falls within the so-called ‘area-based’ contrast policies; that is, aimed at specific geographical areas in disadvantaged conditions.
To identify these areas, many European countries make use of scientific criteria, often considering composite indices, useful for measuring the degree of deprivation or urban poverty. Even if there is no agreement on the set of basic indicators for the construction of these indices [17], in general, this approach has shown that the most deprived areas are not necessarily urban peripheries—as traditionally understood in their geographic and spatial sense—but may also affect central parts of the city.
In the areas subject to intervention, as in the Italian case of complex programs, the planned project actions are both ‘hard measures’, i.e., physical–structural transformations of the neighborhoods or part of them (e.g., demolition, new infrastructure, housing regeneration, etc.), and ‘soft measures’, such as the promotion of social capital (e.g., favoring employment and inclusion of the population).
Urban renewal or regeneration programs in Europe have also been the subject of criticism, especially in relation to the phenomenon of gentrification, i.e., the expulsion of the original inhabitants from the neighborhood undergoing transformation, with the consequent increase in the irregular development of the entire city [18].
According to the most recent vision of the European Union, it is necessary to pursue a unitary approach to urban regeneration to ensure effective interventions. In the panorama of good practices in the EU, it emerges that an effective strategy is to start from actions on parts of cities that are placed, however, always in a dynamic relationship with the entire urban organism, of which they are an integral part, in order to overcome the risk of fragmentation and dispersion of interventions [15,19]. In this sense, the importance of urban planning is better understood in defining appropriate counter actions.
In Italy, where national legislation for urban regeneration is still lacking, there are generally no scientific criteria for the identification of intervention areas, which is usually left to the municipal authorities, on the occasion of sporadic calls for public funding [20,21]. As a result, urban regeneration interventions translate into operations mainly driven by convenience in real estate transformations. To counter this phenomenon, the technical literature proposes the use of multi-criteria evaluations of project proposals, capable of rationalizing choices driven by conflicting objectives, with the aim of maximizing public benefits. Among the various techniques, the use of the analytical hierarchy process (AHP) is frequent [22,23,24,25,26,27,28,29]. In fact, compared to other models, the AHP allows the choice of the best design alternative by considering a greater number of criteria [30], a circumstance frequently found in the analysis of a complex urban program.
However, in light of the new urban geography, urban regeneration interventions must be targeted primarily at areas that have a significant coexistence of degradation factors [31,32]. Consequently, the decision-makers choice of the best design alternative must be informed by the knowledge of pre-existing vulnerability levels and oriented towards the solution that maximizes their reduction [33,34,35,36,37,38,39]. This is possible by integrating the phase of interventions planning in the most vulnerable areas with that of the multi-criteria evaluation of the most effective project. This integration is the basis of this work.
This contribution is part of a wider research project, which proposes a methodology for the localization of areas subject to urban regeneration through the analysis of peripheralization risk. According to this approach, priority areas are those with the greatest aggregated vulnerability, due to the combination of social, building, and urban vulnerabilities. Vulnerability is measured with reference to a composite index, constructed from quantitative indicators, describing the potential degradation factors in the social, building, and urban domains of the city [40].
The objective of this paper is to provide a decision support model for evaluating the effectiveness of urban regeneration programs in areas with a high peripheralization risk. To this end, the following Section 2 proposes a set of indicators for the mitigation of the social, building, and urban vulnerability. Section 3 shows the model for the analysis of design alternatives. The model is defined with the aim of selecting the investment best able to pursue the peripheralization risk mitigation objectives. At this point, the protocol is tested with reference to a case study. In particular, the problematic issues of the investigation area are presented in Section 4, while Section 5 reports the implementation of the calculation algorithms. The results of the application are discussed in Section 6, which is followed by the conclusions of the study with specific indications on research prospects (Section 7).

2. Mitigation Indicators of Social, Building, and Urban Vulnerability

This work proposes a set of mitigation indicators as a useful tool to assess the ability of project actions to reduce vulnerability in social, building, and urban domains and, therefore, to mitigate peripheralization risk. Those mitigation indicators are selected by reference to vulnerability indicators already established for the location of priority urban areas, for which regeneration programs are targeted.
The vulnerability indicators were chosen as part of the research project in which the work is framed, taking into account those proposed: In the technical-scientific literature, to identify degraded urban areas, with regards to the ‘spatial aspects’ of peripheralization processes; in international reports and guidelines, to measure urban sustainability, with regards to the ‘a-spatial aspects’. In general, the criterion that guided the choice of the final set, consisting of 19 vulnerability indicators, was the identification of the critical factors on which it is possible to act through urban and territorial planning. Furthermore, the quality and availability of the data necessary for their measurement at the census section level, the unit chosen for mapping, was taken into account, such that the method was also transferable to geographical contexts other than the Italian one. In fact, the sources of the data necessary to measure these indicators are census data and other data that can be obtained from ordinary urban planning tools, as already documented in a previous contribution by the authors, to which reference should be made for further information [40].
Specifically, vulnerability indicators reveal the potential aptitude for degradation with regards to: The population, for the social dimension; the buildings, for the building domain; and the urban fabric, for the urban domain. More precisely, the indicators proposed to quantify social vulnerability measure the population tendency to live in a condition of socio-economic hardship: Unemployment rate; failure to reach minimum levels of education; and incidence of older people. These indicators relate to several sub-domains, defined factors of social vulnerability: Employment; education, and culture; and composition of the demographic structure.
Building vulnerability indicators refer, instead, to the quality of the building-housing stock. In particular, they measure the state of conservation and technological obsolescence of buildings.
Lastly, indicators for urban domain measure the fragmentation of urban fabric and the composition of the latter, with reference to non-permeable areas. Other indicators selected for this domain are the lack of services and the presence of urban criticalities, such as underutilized, disused, or abandoned areas and solid waste accumulation zones.
The combination of the abovementioned basic indicators, for each domain, makes it possible to obtain composite indices, representing respectively social, building, and urban vulnerability.
By further composing the latter, it is possible to explicate a single synthetic index of aggregated vulnerability.
The spatialization of the obtained indices, on a certain territory, allows to map both single vulnerabilities and both aggregated vulnerabilities, according to different intensity levels.
In addition, intersected with the exposure map, the aggregated vulnerability map leads to the identification of areas most at risk, to which priority actions should be addressed [40].
That said, in this paper, for the three considered domains, mitigation indicators are selected in order to quantitatively measure the vulnerability factors reduction, pursued by an urban regeneration program. The choice is made with specific reference to the previously defined vulnerability indicators but selecting those on which it is possible to act through a regeneration program, therefore the total number of mitigation indicators is reduced to 10, as better specified below.
With respect to the social domain, the proposed mitigation indicators quantify actions aimed at improving the following:
  • Employment, in terms of number of new employees (IMs1);
  • Education, as the number of new graduates in the first-grade secondary school (IMs2);
  • Demographic structure, as capacity of the physical-functional organization to attract young families (IMs3).
The last action can be expressed with a qualitative judgment, which is associated with a proportional value on a scale from 1 to 7. It is the only qualitative indicator out of the total of those proposed.
With regard to the building domain, indicators measure the interventions that determine an improvement of buildings state of conservation and their technological obsolescence, in terms of:
  • Number of buildings with historical, architectural, or artistic value subject to restoration (IMb1);
  • Number of residential buildings subject to maintenance interventions (IMb2);
  • Improper housing recovered and/or subject to health and hygiene improvements (IMb3).
For the urban domain, indicators measure actions aimed to:
  • The reduction of urban fabric fragmentation (IMu1);
  • The increase in permeable green spaces (IMu2);
  • The improvement of the supply of services for population (IMu3);
  • The recovery of abandoned and/or degraded areas, such as areas with waste accumulation and potentially contaminated sites (IMu4).
The novel dataset of the defined mitigation indicators is presented in Table 1.
The necessary data to quantify the aforementioned mitigation indicators can be obtained by analyzing the urban regeneration programs under the decision-maker’s examination

3. An Innovative Model for the Optimal Selection of Design Alternatives for Vulnerability Mitigation

Once the mitigation indicators have been defined, the procedure is divided into the phases of the AHP method: Structure the problem hierarchically; build the decision matrix; compare judgements; and summarize priorities [41].
The hierarchy definition is a fundamental phase for modeling a complex problem [42]. In the proposed methodology, the dominance hierarchy consists of three levels (Figure 1).
At the highest level there is the goal, which in this case is to evaluate the best design alternative in terms of peripheralization risk mitigation in the social, building, and urban domains. At the second level there are the criteria (Ci), which correspond to the vulnerability domains: The social criterion (Cs); the building criterion (Cb); and the urban criterion (Cu). At the third level, there are the sub-criteria, corresponding to mitigation indicators (Cij = IMij), in which there are three for the social criterion (Cs1 = IMs1, Cs2 = IMs2, Cs3 = IMs3), three for the building criterion (Cb1 = IMb1, Cb2 = IMb2, Cb3 = IMb3), and four for the urban criterion (Cu1 = IMu1, Cu2 = IMu2, Cu3 = IMu3, Cu4 = IMu4). The 10 overall sub-criteria are measurable for each k-th design alternative among which the decision maker is called to choose, in order to mitigate vulnerability component of risk for the study area.
The quantitative values of mitigation indicators for each design alternative are at the terminal level of the hierarchy and constitute the lines of the decision matrix. The comparison between the judgments has the aim of measuring the relative importance of criteria and sub-criteria with respect to the general objective. For this purpose, with reference to the decision matrix, this phase is divided into further sub-phases: Pairwise comparison of the design alternatives with respect to each sub-criterion; pairwise comparison of sub-criteria; pairwise comparison of criteria; and synthesis of priorities.
In the calculation of the orders, each proposal has a priority equal to:
PPk: ∑ wPkij × wCij × WCi
where
  • PPk = priority of the k-th project proposal
  • wPkij = normalized vector of sub-criteria for each project proposal
  • wCij = normalized vector of sub-criteria for each domain
  • WCi = normalized vector of criteria
  • (with k = 1, …, n; i = s, b, u; j = 1, …, 4)
The last phase consists of choosing the best design alternative on the basis of the evaluation carried out (Figure 2).

4. Study Area and Project Alternatives

The case study concerns an area of Marcianise Municipality, belonging to the Caserta conurbation in Campania Region (Italy), which is located close to the Metropolitan Area of Naples.
It is a conurbation of 16 municipalities resulting from the merger, which began after the war, of the neighboring municipalities to the city of Caserta, the capital of the same name province. The Caserta conurbation is considered one of the most complex territories in Italy, because of lack of employment, urban disorder, and significant environmental pollution, due to existing production activities and the often illegal disposal of municipal solid waste [43].
The intervention area is located in an urban continuum, bordering Municipalities of San Marco Evangelista and Capodrise. It is delimited to the east by the motorway axis, Naples-Rome route, and by an industrial agglomeration, while, on the remaining three sides, it is connected to the surrounding urban fabric by road axes (Figure 3).
The area in question, with a surface of approximately 50 ha, is the largest of the three, which were identified as priorities for intervention in Marcianise Municipality, by the analysis of peripheralization risk conducted as part of the research project in which this contribution is framed (Figure 4).
The analysis of the most recent municipal urban planning instrumentation shows that the study area is subject to a complex program, in particular an Urban Recovery Program (PRU), due to the conditions of overall degradation by which it is affected. This circumstance validated the high peripheralization risk, already demonstrated through the analysis carried out for the Marcianise Municipality [40]. Therefore, among the three areas found to be at risk R3 and R4, the aforementioned area is selected as a case study in this work, being already destined for an urban regeneration intervention by policy makers, called upon to choose between different design alternatives.
From the analysis of the cognitive framework of the area targeted for the PRU, made available by the Marcianise Municipality [44], it emerges that there is significant social degradation due to the lack of employment and the lack of attractiveness for the younger generations. This confirms the high social vulnerability resulting from the previously carried out risk analysis.
With reference to the urban domain, the cognitive framework confirms the high vulnerability. In fact, the area under examination is characterized by a mainly residential consolidated urban fabric, with some unbuilt enclosed lots in a state of neglect and decay. The fabric is fragmented at the edges and made up of large, completely waterproof surfaces that generate heat islands. Furthermore, there are several disused public areas and structures in conditions of evident degradation. The study area also includes urban planning standards, which, however, are not sufficient according to current legislation. The structure of the study area results from the implementation of an economic and popular building plan, foreseen by the General Town Plan pursuant to the law of 18 April 1962, n. 167.
As a consequence, a high percentage of public residential buildings (IACP) can be noted, which are in a fairly good state of conservation, as are the other private buildings in the study area. This circumstance confirms the low degree of building vulnerability, resulting from the risk analysis carried out.
The three urban regeneration project proposals under consideration by the decision maker are: The PRU, corresponding to the P1 project proposal (Figure 5); two subsequent modifications of the same PRU, corresponding to P2 and P3 project proposals, respectively in Figure 6 and Figure 7.
The examination of the three project proposals shows that each of them presents a plurality of interventions, but it is possible to identify specific guiding principles. P1 proposal pays particular attention to the de-sealing of completely impervious surfaces. P2 proposal gives emphasis to social animation, making the study area highly attractive to young families thanks to the creation of jobs and greater reception in schools. P3 proposal emphasizes the increase in services of collective interest.

5. Application of the Model

The application of the model to the study area requires a careful analysis of the interventions foreseen in each of the three project proposals to be examined by the decision maker. This operation allows to determine the value of the mitigation indicators for each of the three design alternatives, so as to construct the decision matrix. From the latter, the matrices useful for the comparison between sub-criteria and criteria with respect to the general objective are extrapolated.
In this way, the vectors wPkij, wCij, WCi are defined, in order to apply the formula (1) and obtain the priority of each proposal. The individual phases mentioned above are clarified in detail in the following paragraphs.

5.1. Construction of the Decision Matrix

The values of mitigation indicators, for each design alternative, constitute the lines of the decision matrix, while the columns refer to the value of a single sub-criterion for each of the three Pk proposals (with k = 1, 2, 3).
For the implementation of the model it is necessary to derive a scalarized matrix. For this purpose, the sub-criteria values expressed according to a qualitative assessment can be replaced with the relative values obtained through a judgment scale. This is the case of Cs3 sub-criterion, which is low for P1 proposal, high for P2 proposal, and medium-high for P3 proposal. The corresponding scores are 3, 7, and 6 (Table 2).

5.2. Pairwise Comparison of the Design Alternatives

We now proceed to the pairwise comparison of Pk design alternatives with respect to each sub-criterion. Hence, for the 10 sub-criteria, there are 10 comparison matrices. The latter are 3×3 matrices, in which the Pi appear, both in line and in column, while the aij elements represent the dominance coefficients. Thus, the values of individual columns are obtained from the scalarized decision matrix: An example, for the values of the Cs1 subcriterion, is in Table 3. We then proceed to the comparison between the different alternatives using the Saaty semantic scale (Table 4).
After positioning the two compared values on this scale, if they are in the same band, the dominance coefficient aij of each value with respect to the other is 1; if there is one band, aij is 3 for the highest value, it is reciprocal for the lowest value; if there are two bands, the coefficient has a value of 5 for the highest value, 1/5 for the lowest value, and so on. The intermediate coefficients express intermediate situations.
The main diagonal of the matrix is obviously identical, and the property of coefficients reciprocity applies. As an example, Figure 8 shows the comparison between P1 and P2.
In the same way, the comparison matrix for the Cs1 sub-criterion is developed (Table 5).
Each matrix can be normalized using the simplified Fishburn method: Each cell must be divided by the sum of the corresponding column values [45]. The arithmetic mean of each line is then calculated. By repeating this operation for each of the 10 matrices, the wPkij vector is composed (Table 6).
At this point, the consistency of the matrix is checked. It is verified in all cases since the consistency ratio is less than 5, which is the limit of the rank 3 matrices [46].

5.3. Pairwise Comparison of Sub-Criteria

The pairwise comparison of sub-criteria belonging to the same domain aims to establish their mutual importance. Therefore, three matrices are built, one for each criterion or domain. In the matrices for the pairwise comparison of sub-criteria, the dominance coefficients are assumed equal to 1. As in the previous comparison, applying the Fishburn method and carrying out the arithmetic mean for each line, the wCij vector is composed. Table 7 shows the example relating to the social criterion. It should be noted that, for the latter, three sub-criteria have been defined (Cs1, Cs2, Cs3), to which it was chosen to attribute equal importance. Therefore, the normalized matrix presents values that are all equal to 1/3. This also applies to the building criterion, for the same logic. For the urban criterion, according to a similar reasoning, the normalized matrix has values that are all equal to 1/4. In this case, it is verified that the consistency ratio is lower than 5 for the rank 3 matrices (social and building domains) and less than 9 for the rank 4 matrix (urban domain).

5.4. Pairwise Comparison of Criteria

The pairwise comparison of criteria aims at establishing the importance of one domain over the other. Two different scenarios are proposed, in order to reduce the evaluation subjectivity.
In scenario 0, all criteria are of equal importance. After building the pairwise comparison matrix of criteria with the same procedure previously seen, we proceed similarly with the normalization and calculation of the arithmetic mean of each line, composing the WCi vector (Table 8). Even in this case, since there are three criteria (Cs, Cb, Cu) and in Scenario 0, they have the same importance, the matrix corresponding to this scenario has values that are all equal to 1/3. As it is a matrix of rank 3, it is verified that the consistency ratio is less than 5.
Therefore, Scenario 1 is proposed, in which different importance is attributed to the social, building, and urban criteria, depending on the pre-existing vulnerability level in the corresponding social, building, and urban domains. The vulnerability level is that resulting from the peripheralization risk analysis. Vulnerability maps, for each domain, return different vulnerability classes: Low-medium-high-very high. The higher the vulnerability of a specific domain is, the more important the actions addressed to that particular domain are. Low, medium, high, and very high values can be converted into proportional scalar values. Specifically, the scalars 1, 2, 3, and 4 correspond respectively to the low, medium, high, and very high values. Then, we proceed with the comparison in pairs between vulnerability classes, with the ultimate aim to establish the relative importance of the elements according to the scale in Figure 9. This figure allows you to divide the four intervals 1 (low), 2 (medium), 3 (high), and 4 (very high) into the 5 typical Saaty value ranges 0–0.8–1.6–2.4–3.2–4 returned in the lower part of the figure. In this way, it is possible to obtain a support matrix for the decision maker (Table 9).
The analysis of vulnerability maps for the case study shows the presence of potential social and urban degradation, while the building vulnerability is low (Figure 4).
Thus, in Scenario 1, the social criterion is high, the building criterion is low, and the urban criterion is high. Table 10 represents the comparison matrix between criteria.
Like Scenario 0, we proceed by normalizing the matrix and averaging. Then, the WCi vector is composed (with i = s, b, u), obtaining the final matrix in Table 11, whose consistency is also verified.

5.5. Summary of Priorities

In order to evaluate priority of one project proposal over the other, the principle of hierarchical composition is used. The formula (1) already defined for the calculation of PPk is applied, determining the importance of each element of the hierarchy in relation to the objective. Finally, with reference to the proposed scenarios, the related summary matrices are obtained (Table 12 and Table 13). By observing these matrices, it can be noticed that all values are equal, except the row corresponding to the WCi vector and the priority column. The values are the same because the sub-criteria have been given equal importance, therefore equal weight, both in the comparison between project proposals in relation to each sub-criterion, both in the comparison between the sub-criteria. Instead, the values of the WCi vector change because in Scenario 0 the same importance is attributed to the criteria, while in Scenario 1, the criteria are weighted according to the pre-existing vulnerability level. Consequently, the values in the priority column are also different.

6. Results and Discussion

Scenario 0 highlights how the best design alternative is P2: P2 alternative is of 0.09 priority over P3, while P2 is twice the distance from the P1 alternative (Figure 10).
In Scenario 1, the most effective project proposal is still P2 alternative. However, compared to Scenario 0, there is a greater dominance of P2 proposal over P3 proposal. On the other hand, the difference between P1 and P2 remains almost unchanged (Figure 11).
So, the analysis returns the same hierarchical order, only with more marked distances in Scenario 1 compared to Scenario 0. This is because Scenario 1 maximizes the reduction of pre-existing vulnerability levels. In fact, P2 design alternative poses greater attention to the resolution of social and urban problems, where there are higher levels of vulnerability for the area in question.
The P2 and P3 proposals are quite similar to each other in terms of the number of interventions, almost double compared to those of the P1 proposal, in which the redevelopment of the IACP buildings is not foreseen, and not even some services for the community, present instead in the others two proposals.
However, when less importance is given to the building criterion (Scenario 1), it emerges that the P2 proposal ensures a more effective reduction of the pre-existing vulnerability levels for the area in question.
The mitigation indicators and the hierarchical model here described are proposed specifically to allow comparison between alternative projects in order to mitigate the social, building, and urban critical issues of an intra-city area. By measuring these indicators and applying the proposed model, it is possible to quantify the real extent of the interventions in relation to risk mitigation. This allows for an easier decision, especially when the design alternatives seem similar.
With respect to the multicriteria methods already used in the technical literature to evaluate urban regeneration programs, described in Section 1, the main novelty of the work is the approach pursued, based on the integration between the localization phase of the interventions and the evaluation phase of the most effective project. Such an approach, on the one hand, allows to operate where it is a priority; on the other, it makes the decision an intelligent process, which is informed of the pre-existing vulnerability levels. This allows the decision maker to select the design alternative that minimizes the actual vulnerability of an urban area, giving greater emphasis to the truly necessary interventions. In this way, in addition to effectively mitigating the risk, it is possible to optimize the economic resources to be invested in the implementation of the project actions.
However, it should be clarified that the proposed methodology presupposes the prior identification of priority areas of regeneration interventions, which coincide with those with the highest peripheralization risk. Given that a high risk level depends on a significant aggregated vulnerability, the methodology used to estimate the latter is fundamental. This is particularly true as there is no agreement in the international scientific community both on the most suitable set of vulnerability indicators and on the methods of combining them. In the broader research project into which the work is framed, a set of indicators has already been proposed with reference to the three social, building, and urban domains, and a method of combining them based on fuzzy logic is carried out to manage the uncertainty related to the vulnerability assessment [40].
Despite this, quantitative knowledge of the fragility of urban areas in the social, building, and urban dimensions is fundamental for building truly effective mitigation scenarios, contemporary challenges of Urban Intelligence, and Urban Knowledge.
Furthermore, this knowledge allows to reduce the subjectivity of the multicriteria evaluation model implemented according to the AHP logic.
It is also interesting to note that urban regeneration interventions can also have negative effects over time, in particular in relation to the aforementioned phenomenon of gentrification. The proposed support model for decision makers in choosing the most effective design alternative is specifically aimed at selecting the urban regeneration program that maximizes the reduction of pre-existing vulnerability levels. However, another factor to be taken into account in the decision may be to what extent the interventions produce negative effects, such as the expulsion of the original inhabitants due to the increase in property value. Several strategies are proposed in the technical literature and in practice to mitigate the displacement phenomenon, including avoiding the demolition and privatization of public housing buildings; initiating awareness campaigns regarding speculative interventions; establishing anti-eviction zones [47]; and providing for specific anti-displacement programs, including private initiatives [48,49]. In the case study, none of the project proposals being examined by the decision maker envisages the demolition or privatization of the IACP buildings, for which redevelopment with public funds is also planned in the proposals P2 and P3. This feature can certainly help to ensure a certain social mix in the study area and to mitigate the gentrification resulting from the implementation of the interventions. Although, the pursuit of the latter objective is not expressly declared by the municipality of Marcianise.

7. Conclusions

The research proposes a decision support tool based on the AHP method to evaluate the effectiveness of urban regeneration interventions envisaged in areas where the levels of peripheralization risk are significant. Specifically, the effectiveness of the interventions in terms of mitigation of the pre-existing vulnerability is assessed, in the social, building, and urban dimensions.
For this purpose, a set of mitigation indicators is defined, with reference to each vulnerability factor considered for the location of priority areas of intervention. Mitigation indicators are selected in order to analytically estimate the benefits that the projects are capable of generating, in terms of lowering vulnerability indicators values.
Once the values of the mitigation indicators have been clarified, the study proposes a multi-criteria model for the choice between possible urban regeneration interventions. The model is based on hierarchical analysis algorithms, which allow the management of a significant number of indicators. The proposed model has the advantage of determining the design solution that maximizes the reduction of pre-existing vulnerability levels. Furthermore, the best solution selected is the ideal alternative with which to compare different proposed solutions.
The application of the proposed method to the case study demonstrates that design alternatives apparently similar in number and type of interventions may have different effectiveness in relation to the reduction of social, building, and urban vulnerability.
The selection of the mitigation indicators set is carried out in order to build a complete, non-redundant, and coherent set, so as to favor consistency in the subsequent hierarchical analysis. Furthermore, the indicators set is generalized for an urban regeneration intervention and can also be used for monitoring the improvement effects produced by the same intervention on the individual vulnerability factors.
Research developments lie in the integration, in the proposed analysis scheme, of specific indicators measuring mitigation of other potential degradation factors, such as those relating to energy poverty and environmental justice [50,51,52], which certainly can contribute to determining peripheral conditions.
In addition, further investigations of the work may concern how to take into account, in the decision-making process, the extent to which the interventions are able to mitigate any negative effects produced by the interventions themselves over time, such as the phenomenon of gentrification. This aspect is of fundamental importance to discourage the creation of peripheral conditions determined by factors of social vulnerability in other parts of the city.

Author Contributions

Conceptualization, R.G. and A.N.; data curation, R.G., A.N., A.M., and M.C.; formal analysis, R.G., A.N., A.M., and M.C.; investigation, A.M. and M.C.; methodology, R.G., A.N., A.M., and M.C.; software, A.M. and M.C.; supervision, R.G. and A.N.; validation, R.G. and A.N.; visualization, A.M. and M.C.; writing—original draft, R.G., A.N., and A.M.; writing—review and editing, R.G., A.N., and A.M. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Gerundo, R. I Programmi Urbani Complessi (Complex Urban Programs); Graffiti: Napoli, Italy, 2000. [Google Scholar]
  2. Guiducci, R. Periferie Tra Degrado e Riqualificazione (Peripheries between Decay and Redevelopment); Laterza: Bari, Italy, 1993. [Google Scholar]
  3. Oliva, F. Il sistema insediativo (The settlement system). In Progettazione Urbanistica. Teorie e Tecniche (Urban Planning. Theories and Techniques); Selicato, F., Rotondo, F., Eds.; McGrawHill: Milan, Italy, 2010. [Google Scholar]
  4. Taylor, P.J.; Lang, R.E. The shock of the new: 100 concepts describing recent urban change. Environ. Plan. 2004, 36, 951–958. [Google Scholar] [CrossRef]
  5. Geneletti, D.; La Rosa, D.; Spyra, M.; Cortinovis, C. A review of approaches and challenges for sustainable planning in urban peripheries. Landsc. Urban Plan. 2017, 165, 231–243. [Google Scholar] [CrossRef]
  6. Gerundo, R.; Marra, A. Il rischio nei fenomeni di periferizzazione delle aree urbane e metropolitane (The risk of peripheralization processes in urban and metropolitan areas). Urban. Inf. 2018, 278, 338–342. [Google Scholar]
  7. Copus, A.K. From Core-periphery to Polycentric Development. Concepts of Spatial and Aspatial Peripherality. Eur. Plan. Stud. 2001, 9, 539–552. [Google Scholar] [CrossRef]
  8. Kühn, M.; Bernt, M. Peripheralization and power—Theoretical debates. In Peripheralization: The Making of Spatial Dependencies and Social Injustice; Fischer-Tahir, A., Naumann, M., Eds.; Springer Fachmedien Wiesbaden: Wiesbaden, Germany, 2013; pp. 302–317. [Google Scholar]
  9. Bernt, M.; Colini, L. Exclusion, Marginalization and Peripheralization. Conceptual Concerns in the Study of Urban Inequalities; Working Paper; Leibniz Institute for Regional Development and Structural Planning: Erkner, Germany, 2013. [Google Scholar]
  10. Kühn, M. Peripheralization: Theoretical concepts explaining socio-spatial inequalities. Eur. Plan. Stud. 2015, 23, 367–378. [Google Scholar] [CrossRef]
  11. Baharaoglu, D.; Kessides, C. Urban Poverty. In A Sourcebook for Poverty Reduction Strategies; World Bank: Washington, DC, USA, 2002; Chapter 16. [Google Scholar]
  12. Townsend, P. Deprivation. J. Soc. Policy 1987, 2, 125–146. [Google Scholar] [CrossRef]
  13. Ministry of Housing, Communities and Local Government. The English Indices of Deprivation 2019. Statistical Release. 2019. Available online: https://assets.publishing.service.gov.uk/government/uploads/system/uploads/attachment_data/file/835115/IoD2019_Statistical_Release.pdf (accessed on 30 April 2020).
  14. European Commission-EU. Guidelines on Best Practice to Limit, Mitigate or Compensate Soil Sealing; European Commission-EU; Publication Office: Luxembourg, 2012. Available online: https://ec.europa.eu/environment/soil/pdf/guidelines/pub/soil_en.pdf (accessed on 30 July 2020).
  15. European Commission. Integrated Regeneration of Deprived Areas and the New Cohesion Policy Approach. An URBACT contribution to the European Urban Agenda; Publications Office: Luxembourg, 2015. Available online: https://urbact.eu/sites/default/files/20150909_urbact_deprived-areas_gb_md_1.pdf (accessed on 30 July 2020).
  16. United Nations-UN. New Urban Agenda; A/RES/71/256; United Nations (UN): New York, NY, USA, 2017. Available online: http://habitat3.org/wp-content/uploads/New-Urban-Agenda-GA-Adopted-68th-Plenary-N1646655-E.pdf (accessed on 30 July 2020).
  17. Cordoba Hernández, R.; Gonzáles García, I.; Guerrero Periñan, G. Urban Poverty Partnership: Report about Urban Deprivation/Poverty Observatories in the European Union; E.T.S. Arquitectura (UPM); European Commission: Brussels, Belgium, 2018; Available online: https://ec.europa.eu/futurium/en/urban-poverty/report-about-urbandeprivationpoverty-observatories-eu-universidad-politecnica-de (accessed on 30 July 2020).
  18. Smith, N. The New Urban Frontier. Gentrification and the Revanchist City; Routledge: London, UK, 1996. [Google Scholar]
  19. Tosics, I. Dilemmas of Integrated Area-Based Urban Renewal Programmes. In The Urbact Tribune; European Union, Urbact: Saint-Denis, France, 2009. [Google Scholar]
  20. Decree of the Italian Prime Minister n. 249, 15 October 2015. Interventi per la Riqualificazione Sociale e Culturale delle Aree Urbane Degradate (Interventions for the Social and Cultural Requalification of Degraded Urban Areas). Available online: http://www.mit.gov.it/sites/default/files/media/notizia/2016-01/dpcm_15_ottobre_2015.pdf (accessed on 30 April 2020).
  21. Decree of the Italian Prime Minister, 25 May 2016. Bando per la Presentazione di Progetti per la Predisposizione del Programma Straordinario di Intervento per la Riqualificazione Urbana e la Sicurezza delle Periferie delle Città Metropolitane e Dei Comuni Capoluogo di Provincia (Call for the Presentation of Projects for the Preparation of the Extraordinary Intervention Program for Urban Redevelopment and Safety of the Peripheries of Metropolitan Cities and Provincial Capitals). Available online: http://www.governo.it/sites/governo.it/files/Bando_periferie_urbane.pdf (accessed on 30 April 2020).
  22. Nijkamp, P.; Rietveld, P.; Voogd, H. Multicriteria Evaluation in Physical Planning; North Holland Publications: Amsterdam, The Netherlands, 1990. [Google Scholar]
  23. Vincke, P. Multicriteria Decision-Aid; John Wiley & Sons, Inc.: New York, NY, USA, 1992. [Google Scholar]
  24. Tzeng, G.H.; Huang, J.J. Multiple Attribute Decision Making Methods and Applications; CRC Press, Taylor & Francis Group: New York, NY, USA, 2011. [Google Scholar]
  25. Stanghellini, S.; Mambelli, T. La Valutazione dei Programmi di Riqualificazione Urbana Proposti dai Soggetti Privati (The Evaluation of the Urban Regeneration Programs Proposed by Private Entities); Franco Angeli: Milan, Italy, 2003. [Google Scholar]
  26. De Mare, G.; Nesticò, A.; Tajani, F. Building Investments for the Revitalization of the Territory: A Multisectoral Model of Economic Analysis. In Part III: Lecture Notes in Computer Science, Proceedings of ICCSA 2013 International Conference Computational Science and Its Applications, Ho Chi Minh City, Vietnam, 24–27 June 2013; Murgante, B., Misra, S., Carlini, M., Torre, C., Nguyen, H.Q., Taniar, D., Apduhan, B.O., Gervasi, O., Eds.; Springer: Berlin/Heidelberg, Germany, 2013; Volume 7973, pp. 493–508. [Google Scholar] [CrossRef]
  27. Guarini, M.R.; Nesticò, A.; Morano, P.; Sica, F. A Multicriteria Economic Analysis Model for Urban Forestry Projects. In New Metropolitan Perspectives, Proceedings of ISHT 2018 International Symposium on New Metropolitan Perspectives, Reggio Calabria, Italy, 22–25 May 2018; Part of Smart Innovation, Systems and Technologies Book Series; Calabrò, F., Della Spina, L., Bevilacqua, C., Eds.; Springer: Cham, Switzerland, 2018; Volume 100, pp. 564–571. [Google Scholar] [CrossRef]
  28. Nesticò, N.; Sica, F. The sustainability of urban renewal projects: A model for economic multi-criteria analysis. J. Prop. Investig. Financ. 2017, 35, 397–409. [Google Scholar] [CrossRef]
  29. Nesticò, A.; Maselli, G. Sustainability indicators for the economic evaluation of tourism investments on islands. J. Clean. Prod. 2020, 248, 119217. [Google Scholar] [CrossRef]
  30. Nesticò, N.; Somma, P. Comparative Analysis of Multi-Criteria Methods for the Enhancement of Historical Buildings. Sustainability 2019, 11, 4526. [Google Scholar] [CrossRef] [Green Version]
  31. United Nations Human Settlements Programme. The Fundamentals of Urbanization. Evidence Base for Policy Making; UN-Habitat: Nairobi, Kenya, 2016; ISBN 978-92-1-132730-4. Available online: https://unhabitat.org/the-fundamentals-of-urbanization-evidence-base-for-policy-making (accessed on 30 April 2020).
  32. Conway, M.; Konvitz, J. Meeting the Challenge of Distressed Urban Areas. Urban. Stud. 2000, 37, 749–774. Available online: https://EconPapers.repec.org/RePEc:sae:urbstu:v:37:y:2000:i:4:p:749-774 (accessed on 30 April 2020). [CrossRef]
  33. Office of the United Nations Disaster Relief Coordinator. Natural Disasters and Vulnerability Analysis: Report of Expert Group Meeting, 9–12 July 1979; United Nations: Geneva, Switzerland, 1980. Available online: https://digitallibrary.un.org/record/95986 (accessed on 30 April 2020).
  34. Gerundo, R.; Fasolino, I. Sicurezza Territoriale ed Efficienza Urbanistica (Territorial Safety and Urban Efficiency); Edizioni Scientifiche Italiane: Napoli, Italy, 2010. [Google Scholar]
  35. Gerundo, R.; Grimaldi, M.; Marra, A. A methodology hazard-based for the mitigation of the radon risk in the urban planning. UPLanD-J. Urb. Plan. Landsc. Environ. Des. 2016, 1, 27–38. [Google Scholar] [CrossRef]
  36. Sebillo, M.; Vitiello, G.; Grimaldi, M.; Dello Buono, S. SAFE (Safety for Families in Emergency): A Citizen-Centric Approach for Risk Management. In Part II: Lecture Notes in Computer Science, Proceedings of ICCSA 2019 International Conference Computational Science and Its Applications, Saint Petersburg, Russia, 1–4 July 2019; Misra, S., Gervasi, O., Murgante, B., Stankova, E., Korkhov, V., Torre, C.A.C., Rocha, A.M., Taniar, D.O., Apduhan, B., Tarantino, E., Eds.; Springer Nature: Cham, Switzerland, 2019; Volume 11620, pp. 424–440. [Google Scholar] [CrossRef]
  37. Grimaldi, M.; Sebillo, M.; Vitiello, G.; Pellecchia, V. An Ontology Based Approach for Data Model Construction Supporting the Management and Planning of the Integrated Water Service. In Part VI: Lecture Notes in Computer Science, Proceedings of ICCSA 2019 International Conference Computational Science and Its Applications, Saint Petersburg, Russia, 1–4 July 2019; Misra, S., Gervasi, O., Murgante, B., Stankova, E., Korkhov, V., Torre, C.A.C., Rocha, A.M., Taniar, D.O., Apduhan, B., Tarantino, E., Eds.; Springer Nature: Cham, Switzerland, 2019; Volume 11624, pp. 243–252. [Google Scholar] [CrossRef]
  38. Troisi, R.; Alfano, G. Towns as Safety Organizational Fields: An Institutional Framework in Times of Emergency. Sustainability 2020, 11, 7025. [Google Scholar] [CrossRef] [Green Version]
  39. Sebillo, M.; Vitiello, G.; Grimaldi, M.; De Piano, A. A Citizen-Centric Approach for the Improvement of Territorial Services Management. ISPRS Int. J. Geo-Inf. 2020, 9, 223. [Google Scholar] [CrossRef] [Green Version]
  40. Gerundo, R.; Marra, A.; De Salvatore, V. Construction of a Composite Vulnerability Index to map Peripheralization Risk in Urban and Metropolitan Areas. Sustainability 2020, 12, 4641. [Google Scholar] [CrossRef]
  41. Saaty, T.L. The Analytic Hierarchy Process; McGraw-Hill: New York, NY, USA, 1980; (Reprinted by RWS Publications: 4922 Ellsworth Avenue, Pittsburgh, PA 15213, USA, 2000). [Google Scholar]
  42. Saaty, T.L. Decision Making for Leaders: The Analytic Hierarchy Process for Decision in a Complex Word; RWS Publications: Pittsburgh, PA, USA, 1999. [Google Scholar]
  43. Rufino, A.; Pizzo, C. Intelligenza Territoriale Come Propulsore di Sviluppo Sostenibile (Territorial Intelligence as a Propeller of Sustainable Development); FrancoAngeli: Milan, Italy, 2012. [Google Scholar]
  44. Marcianise Municipality. Urban Recovery Program—Area 167, Presentation. Available online: http://www.comune.marcianise.ce.it/c061049/zf/index.php/serviziaggiuntivi/index/index/idtesto/2 (accessed on 30 July 2020).
  45. Fishburn, P.C. Additive Utilities with Incomplete Product Set: Applications to Priorities and Assignments; ORSA: Baltimora, MD, USA, 1967. [Google Scholar]
  46. Saaty, T.L. A scaling method for priorities in hierarchy structures. J. Math. Psychol. 1977, 15, 234–281. [Google Scholar] [CrossRef]
  47. LeGates, R.T.; Hartman, C. Gentrification-caused displacement. Urban Lawyer 1982, 14, 31–55. [Google Scholar]
  48. Metropolitan Area Planning Council. Managing Neighborhood Change: Anti-Displacement Strategies; Technical Report; Metropolitan Area Planning Council: Boston, MA, USA, 2015.
  49. Levy, D.K.; Comey, J.; Padilla, S. Keeping the Neighborhood Affordable: A Handbook of Housing Strategies for Gentrifying Areas; The Urban Institute, Metropolitan Housing and Communities Policy Center: Washington, DC, USA, 2006; Available online: www.urban.org/uploadedPDF/411295_gentrifying_areas.pdf (accessed on 30 July 2020).
  50. Gerundo, R.; Fasolino, I.; Grimaldi, M. ISUT Model. A composite index to measure the sustainability of the urban transformation. In Smart Energy in the Smart City. Urban Planning for a Sustainable Future; Papa, R., Fistola, R., Eds.; Springer International Publishing: Cham, Switzerland, 2016; pp. 117–130. [Google Scholar]
  51. Fasolino, I.; Grimaldi, M.; Zarra, T.; Naddeo, V. Odour control strategies for a sustainable nuisances action plan. Glob. NEST J. 2016, 4, 734–741. [Google Scholar] [CrossRef] [Green Version]
  52. Fasolino, I.; Grimaldi, M.; Zarra, T.; Naddeo, V. Implementation of integrated nuisances action plan. Chem. Eng. Trans. 2016, 54, 19–24. [Google Scholar] [CrossRef]
Figure 1. Hierarchical structure of the proposed model.
Figure 1. Hierarchical structure of the proposed model.
Sustainability 12 08024 g001
Figure 2. Workflow of the proposed methodology.
Figure 2. Workflow of the proposed methodology.
Sustainability 12 08024 g002
Figure 3. Territorial context of the study area.
Figure 3. Territorial context of the study area.
Sustainability 12 08024 g003
Figure 4. Peripheralization risk map of Marcianise Municipality and levels of social, building, and urban vulnerability for the study area. Own elaboration on data from Gerundo et al. ii: Construction of a Composite Vulnerability Index to map Peripheralization Risk in Urban and Metropolitan Areas [40].
Figure 4. Peripheralization risk map of Marcianise Municipality and levels of social, building, and urban vulnerability for the study area. Own elaboration on data from Gerundo et al. ii: Construction of a Composite Vulnerability Index to map Peripheralization Risk in Urban and Metropolitan Areas [40].
Sustainability 12 08024 g004
Figure 5. Planimetric scheme of the P1 project proposal.
Figure 5. Planimetric scheme of the P1 project proposal.
Sustainability 12 08024 g005
Figure 6. Planimetric scheme of the P2 project proposal.
Figure 6. Planimetric scheme of the P2 project proposal.
Sustainability 12 08024 g006
Figure 7. Planimetric scheme of the P3 project proposal.
Figure 7. Planimetric scheme of the P3 project proposal.
Sustainability 12 08024 g007
Figure 8. Graduated scale for the comparison between P1 and P2 in relation with the Cs1 sub-criterion.
Figure 8. Graduated scale for the comparison between P1 and P2 in relation with the Cs1 sub-criterion.
Sustainability 12 08024 g008
Figure 9. Positioning of scalar values on the Saaty graduated scale.
Figure 9. Positioning of scalar values on the Saaty graduated scale.
Sustainability 12 08024 g009
Figure 10. Best alternative for Scenario 0.
Figure 10. Best alternative for Scenario 0.
Sustainability 12 08024 g010
Figure 11. Best alternative for Scenario 1.
Figure 11. Best alternative for Scenario 1.
Sustainability 12 08024 g011
Table 1. Mitigations indicators, unit of measurement, and definition.
Table 1. Mitigations indicators, unit of measurement, and definition.
Mitigation IndicatorU.M.Definition
Social Domain IMs1New employeesn.Number of new employees in the age group corresponding to the workforce
IMs2New graduates at secondary school cycle (middle school)n.Population of 15 years and over who will obtain
a middle school diploma per year
IMs3Ability to attract
young families
Qualitative judgement (value)Ability to attract young families of city
physical-functional structure:
1, very shoddy: the setting up of young families is strongly discouraged;
2, shoddy: the structure discourages the settlement of young families;
3, very low: the structure has no significant effect on the attraction of young families;
4, low: the city structure is suitable for the settlement of young families;
5, medium: the city structure is particularly suitable for the settlement of young families;
6, medium high: the setting up of young families is encouraged;
7, high: the setting up of young families is
strongly encouraged.
Building DomainIMb1Recovered buildings of
historical, architectural
or artistic value
n.Number of buildings with historical, architectural or artistic value subject to restoration.
IMb2Recovered residential buildings in bad and mediocre conservation staten.Number of residential buildings subject to extraordinary maintenance or renovation
IMb3Improper housing
recovered
n.Number of improper housing subject to health and hygiene improvements.
Urban DomainIMu1Edge Densitym/haRatio between total sum of perimeters of the polygons of built up areas and the total surface of investigated area.
IMu2Increment of
permeable areas
m2Surface for additional permeable areas.
IMu3Increase in urban planning standardsm2Surface provided for additional urban
planning standards.
IMu4Recovered
urban critical areas
m2Surface of enclosed recovered spaces: abandoned production areas; areas with newly built artifacts that have not been used; undeveloped areas devoid of specific use or abandoned; areas with waste accumulation.
Table 2. Scalarized decision matrix for the case study.
Table 2. Scalarized decision matrix for the case study.
Cs1
[n.]
Cs2
[n.]
Cs3
[value]
Cb1
[n.]
Cb2
[n.]
Cb3
[n.]
Cu1
[m/ha]
Cu2
[m2]
Cu3
[m2]
Cu4
[m2]
P133030050.033713,366.716,164.97059.52
P26250714130.03335549.527,501.87059.52
P3370614150.033411,565.036,852.87059.52
Table 3. Values of criterion Cs1 for each design alternative.
Table 3. Values of criterion Cs1 for each design alternative.
P1P2P3
Cs1336237
Table 4. Semantic scale of Saaty.
Table 4. Semantic scale of Saaty.
Intensity135792-4-6-8
Judgement
of Importance
EqualModerateHighVery HighExtremeIntermediate levels
Table 5. Pairwise comparison matrix of the alternatives for Cs1 sub-criterion.
Table 5. Pairwise comparison matrix of the alternatives for Cs1 sub-criterion.
P1P2P3
P111/61
P2615
P311/51
Table 6. Pairwise comparison matrix of the alternatives for the Cs1 sub-criterion and wPkij vector.
Table 6. Pairwise comparison matrix of the alternatives for the Cs1 sub-criterion and wPkij vector.
P1P2P3wPkij
P10.1250.1220.1430.130
P20.7500.7320.7140.732
P30.1250.1460.1430.138
Table 7. Normalized matrix for pairwise comparison of Cs sub-criteria to obtain wCij vector.
Table 7. Normalized matrix for pairwise comparison of Cs sub-criteria to obtain wCij vector.
Cs1Cs2Cs3wCij
Cs10.3330.3330.3330.333
Cs20.3330.3330.3330.333
Cs30.3330.3330.3330.333
Table 8. Normalized matrix for pairwise comparison of criteria and WCi vector–Scenario 0.
Table 8. Normalized matrix for pairwise comparison of criteria and WCi vector–Scenario 0.
CsCbCuWCi
Cs0.330.330.330.33
Cb0.330.330.330.33
Cu0.330.330.330.33
Table 9. Matrix for assigning weights to the criteria.
Table 9. Matrix for assigning weights to the criteria.
LowMediumHighVery High
Low1.0000.3330.1670.111
Medium3.0001.0000.3330.167
High6.0003.0001.0000.333
Very High9.0006.0003.0001.000
Table 10. Pairwise comparison matrix of criteria—Scenario 1.
Table 10. Pairwise comparison matrix of criteria—Scenario 1.
Cs (High)Cb (Low)Cu (High)
Cs (High)161
Cb (Low)0.16710.167
Cu (High)161
Table 11. Normalized matrix for pairwise comparison of criteria and WCi vector—Scenario 1.
Table 11. Normalized matrix for pairwise comparison of criteria and WCi vector—Scenario 1.
CsCbCuWCi
Cs0.4620.4620.4620.46
Cb0.0770.0770.0770.07
Cu0.4620.4620.4620.46
Table 12. Final synthesis matrix—Scenario 0.
Table 12. Final synthesis matrix—Scenario 0.
CS (social)Ce (Building)Cu (Urban)Priority
Wci0.3330.3330.333
CS1CS2CS3Ce1Ce2Ce3Cu1Cu2Cu3Cu4
wCij0.3330.3330.3330.3330.3330.3330.2500.2500.2500.250
wP10.1300.0910.0740.0530.0530.4550.3330.5910.0800.3330.200
wP20.7320.8180.6430.4740.4740.0910.3330.0750.2650.3330.403
wP30.1380.0910.2830.4740.4740.4550.3330.3340.6560.3330.313
Table 13. Final synthesis matrix—Scenario 1.
Table 13. Final synthesis matrix—Scenario 1.
CS (social)Ce (Building)Cu (Urban)Priority
Wci0.46150.07690.4615
CS1CS2CS3Ce1Ce2Ce3Cu1Cu2Cu3Cu4
wCij0.3330.3330.3330.3330.3330.3330.2500.2500.2500.250
wP10.1300.0910.0740.0530.0530.4550.3330.5910.0800.3330.205
wP20.7320.8180.6430.4740.4740.0910.3330.0750.2650.3330.425
wP30.1380.0910.2830.4740.4740.4550.3330.3340.6560.3330.253

Share and Cite

MDPI and ACS Style

Gerundo, R.; Nesticò, A.; Marra, A.; Carotenuto, M. Peripheralization Risk Mitigation: A Decision Support Model to Evaluate Urban Regeneration Programs Effectiveness. Sustainability 2020, 12, 8024. https://doi.org/10.3390/su12198024

AMA Style

Gerundo R, Nesticò A, Marra A, Carotenuto M. Peripheralization Risk Mitigation: A Decision Support Model to Evaluate Urban Regeneration Programs Effectiveness. Sustainability. 2020; 12(19):8024. https://doi.org/10.3390/su12198024

Chicago/Turabian Style

Gerundo, Roberto, Antonio Nesticò, Alessandra Marra, and Maria Carotenuto. 2020. "Peripheralization Risk Mitigation: A Decision Support Model to Evaluate Urban Regeneration Programs Effectiveness" Sustainability 12, no. 19: 8024. https://doi.org/10.3390/su12198024

APA Style

Gerundo, R., Nesticò, A., Marra, A., & Carotenuto, M. (2020). Peripheralization Risk Mitigation: A Decision Support Model to Evaluate Urban Regeneration Programs Effectiveness. Sustainability, 12(19), 8024. https://doi.org/10.3390/su12198024

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop