Abstract
Composite indicators have been analyzed by several scholars, especially with the aim of defining standardization and aggregation rules consistent to the multidimensional theoretical framework underlying these kind of measures and adequate to the difficulty of comparing data of different nature. Starting from a broadly shared methodology, set up by OECD in 2008, the paper proposes a Composite Indicator of Territorial Vulnerability based on environmental, social and economic criteria. A special attention has been paid to the methodological approach more than to the results, with a focus on uncertainty and sensitivity analysis. The latter one has been developed by the use of the SimLab (http://ipsc.jrc.ec.europa.eu), which has allowed to estimate the probability distribution function of the composite indicator and to point out the field of variation of its variables. Lombardy Region has been selected as a pilot case study since it is one of the Italian regions with the highest infrastructural development. The results show that the Composite Indicator of Territorial Vulnerability applied to municipalities in the Lombardy Region has a limited variation range, and thus low uncertainty. Furthermore, the synthetic measure of territorial vulnerability seems to be a promising decision aid tool in the field of regional infrastructural development policies.
Access provided by CONRICYT-eBooks. Download chapter PDF
Similar content being viewed by others
Keywords
1 The Multidimensional Notion of Territorial Vulnerability
Vulnerability refers to the degree to which communities and individuals are susceptible to the effects of hazardous processes, encompassing the physical, social and organizational components of social systems (Golobič and Breskvar Žaucery 2010; Tavares et al. 2015). At the same time vulnerability refers to the ability to prepare for, respond to, and recover from external events (Cutter et al. 2009; Toro et al. 2011) that have the potential to become worse (Bradley and Smith 2004).
Vulnerability is an “integral part of the causal chain of risk” which can be defined as the product of the level of damage in the conditions of use and the frequency of adverse events (Cutter et al. 2000).
The definition conforms to the following formula:
where R represents the risk, D for damage and F for the frequency of harmful events.
Territorial vulnerability could affect both the frequency and the level of harm Thus, the risk (R) should be commensurate to the degree of territorial vulnerability (V):
According to UNISDR (2012) understanding vulnerability is one of the foundations that support the achievement of the 10 essentials of safe and resilient cities, and is crucial to the development of local plans and policies.
Although the many definitions (Tran et al. 2010) of the notion of vulnerability highlight the different faces of the same concept, they all focus on the following concepts:
-
(i)
vulnerability is an intrinsic feature of a system that can be described by the use of a specific set of criteria;
-
(ii)
the notion of vulnerability is multidimensional as it includes health, education, social assistance, the economy, spatial planning and transportation and their mutual relationships (Millenium Ecosystem Assessment 2005; Cutter et al. 2003; Menoni et al. 2012; Tavares et al. 2015).
The development of infrastructure in a vulnerable context strengthens the risk, as it increases the frequency and the significance of the harmful events. The vulnerability of the territory with respect to the realization of infrastructures can also be associated with land consumption and the impact on the agricultural system as well as on environment (Mazzocchi et al. 2013; Torre et al. 2014; Oppio et al. 2016).
Finally reducing vulnerability is a cost-effective strategy of risk management (Kasperson et al. 2001) and a key element in any risk governance process. Moreover understanding vulnerability is crucial to the development of disaster mitigation plans and policies.
Many scholars attempting to evaluate the sustainability of development policies and programs have underlined the necessity to adopt a multidimensional approach in order to assess their impacts in a comprehensive way. In these kind of decision making processes, environmental, social and economic vulnerability assessment plays a crucial role. Providing an aggregate vulnerability measure, able to tackle all these issues together, is important in policy making and regional planning both from a conceptual and an operational perspective (Granger and Hayne 2001; Munda 2010).
2 Using Composite Indicators for Assessing Territorial Vulnerability
Composite indicators play very important role in policymaking and benchmarking (Freudenberg 2008; Saltelli 2006) as a tool to measure the complexity of environmental and societal phenomena. Despite composite indicators are increasingly used because of their capacity to process a large amount of data and to communicate the outputs of the analysis in a simple way, they could be misleading and poorly reliable if not supported by a robust and clearly stated methodology. Actually, it involves both theoretical and methodological assumption, which need to be assessed carefully to avoid producing results of dubious analytic rigor (Saisana et al. 2005). To overcome this problematic issue, Nardo et al. (2005) propose a Handbook of Composite Indicators (Ci) offering guidelines for composite indicator development. The latter guidelines were then recall in the OECD Guidelines (2008) that summarized pros and cons of using Ci and proposed a comprehensive and robust methodology. According to the OECD Guidelines, “A composite indicator is formed when individual indicators are compiled into a single index on the basis of an underlying model. The composite indicator should ideally measure multidimensional concepts which cannot be captured by a single indicator…”. Many different Ci has been developed in various fields, such as the economy, environment, society and globalization; a complete list is reported in the EU site (http://composite-indicators.jrc.ec.europa.eu/) developed by the Composite Indicator Research Group where a 10-step guide is reported for the formulation of a robust Ci, already tested in several different cases. The guide proposed tries to answer the main issues related to the development of a Ci (Saltelli et al. 2008) such as, (i) the definition of a set of indicators in the index; (ii) the mechanism for including and excluding indicators in the index; (iii) the model choice for estimating the measurement error in the data; (iv) the indicator preliminary treatment; (v) the choice of weights attached to the indicators; (vi) the choice of the aggregation method; (vii) the type of normalization scheme applied to the indicators to remove scale effects. The Checklist for building a composite indicator (EU checklist) and the methodology proposed is reported in Table 1.
In general an index is a function of the underline indicators. Weights are assigned to each indicator to express the relevance of indicators in the context of the phenomena to be measured. As showed in Fig. 1 the first phase of the analysis regards the definition of a theoretical framework, the data selection and the input of missing data. These phases regard the selection of the indicators on the base of the literature and the expert opinions and the quantification of the selected variables.
The third phase is about a multivariate analysis helpful in assessing the suitability of the data set and provides an understanding of the implications of the methodological choices, as weighting and aggregation.
There are many analytical approaches to perform multivariate analysis, among the others Principal Components Analysis (PCA), Factor Analysis (FA), Cluster Analysis (CA). In this work we did perform multivariate analysis using the PCA method, with the double aim of finding the most relevant criteria (variables) and of attaching weights to the criteria before running the aggregation phase. The application of PCA is well described later on.
The normalization phase regards the standardization of the different unites measurement of the indicators in a unique one. Three methodologies will be applied. The first method is the standardization or z-scores. This method converts indicators to a common scale with a mean of zero and standard deviation of one. In this way the values close to the two extremes acquire higher importance than the ones close to the average 0.
For each individual indicator \({\text{x}}_{\text{qc}}^{\text{t}}\), the average across municipalities \({\text{x}}_{\text{qc = c}}^{\text{t}}\) and the standard deviation across countries \(\upsigma_{\text{qc = c}}^{\text{t}}\) are calculated. The normalization formula is
so that all \({\text{I}}_{\text{qc}}^{\text{t}}\) have similar dispersion across municipality.
The second method is the Min-Max normalization. This method brings the values into an interval between 0 and 1.
Each indicator \({\text{x}}_{\text{qc}}^{\text{t}}\) for a generic municipality c and time t is transformed in
where \(min_{\text{c}} \left( {{\text{x}}_{\text{q}}^{\text{t}} } \right)\) and \(max_{\text{c}} \left( {{\text{x}}_{\text{q}}^{\text{t}} } \right)\) are the minimum and the maximum values of \({\text{x}}_{\text{qc}}^{\text{t}}\) across all municipality c at time t.
The last method is called “distance to a reference”. This method of normalization makes use of a benchmark in order to evaluate performances of the countries.
This method takes the ratios of the indicator x tqc for a generic country c and time t with respect to the individual indicator x t0qc=c for the reference country at the initial time t0.
Once the data have been normalized there are still two fundamental steps for the construction of the composite indicator, weighting and aggregating. The first step aims to give different importance to the criteria and several methods are available to make the choice. Some of these methods accept some grade of individual judgment by experts in the specific field when attaching weights to the criteria. Some other methods are instead based on statistical properties, giving more weights to the criteria that are statistically more relevant. For this research, we decided to implement the PCA method to find weights, which are valid by a statistical point of view, to be comparing the outcome then with a linear additive aggregation with no weights applied. In practical terms, we compared a statistical based weighting system to an “equal weights” system, and then two aggregation methods, the linear and the geometrical one. The results are then described.
The more interesting phase is the uncertainty and sensitivity analysis, because when constructing a composite indicator there is always some grade of uncertainty. A combination of uncertainty and sensitivity analysis is used to assess robustness of composite indicators (Del Giudice et al. 2014).
“Uncertainty analysis focuses on how uncertainty in the input factors propagates through the structure of the composite indicator and affects the composite indicator values. Sensitivity analysis assesses the contribution of the individual source of uncertainty to the output variance. While uncertainty analysis is used more often than sensitivity analysis and is almost always treated separately, the iterative use of uncertainty and sensitivity analysis during the development of a composite indicator could improve its structure” (Saisana et al. 2005; Tarantola et al. 2000; Gall 2007).
The results of the robustness analysis are generally reported as country rankings (in our case municipality ranking) with their related uncertainty bounds, which are due to the uncertainties at play. This makes it possible to communicate to the user the plausible range of the composite indicator values for each country. The sensitivity analysis results are generally shown in terms of the sensitivity measure for each input source of uncertainty. These sensitivity measures represent how much the uncertainty in the composite indicator for a given municipality would be reduced if that particular input source of uncertainty were removed. The aim of uncertainty analysis is thus to create a statistically reliable sample to which one can compare the output variance generated by using the real values.
One way of doing this simulation is through Monte Carlo analysis, in which we look at the distribution functions of the input parameters, as derived from the estimation. For example we may have the following scheme:
We start from a factor \(\alpha \sim N\left( {\overline{\alpha } ,\sigma_{\alpha } } \right)\), which reads: after estimation α is known to be normally distributed with mean \(\overline{\alpha }\) and standard deviation σα.
Likewise for factors β, γ, and so on. For each of these factors, we draw a sample from the respective distributions, thus we produce a set of row vectors \(\left( {\alpha^{j} ,\beta^{j} , \ldots } \right)\), with j = 1, 2, …, N in such a way that \(\left( {\alpha^{1} ,\alpha^{2} , \ldots ,\alpha^{N} } \right)\) is a sample from N \(( {\overline{\alpha}, \sigma_{\alpha } } )\) and likewise for the distribution function of the other factors.
We can then compute the model for all vectors \(\left( {\alpha^{j} ,\beta^{j} , \ldots } \right)\) thereby producing a set of N values of a model output Y j .
These steps constitute our uncertainty analysis. Having performed this uncertainty analysis we can then move on to a sensitivity analysis, in order to determine which of the input parameters are more important in influencing the uncertainty in the model output.
There are several methods of sensitivity analysis based on linear regression or correlation. The most important of them are: the PEAR analysis based on simple correlation between the criteria composing the indicator and the output; the PCC analysis based on correlation and partial correlation; the SRC method based on regression analysis.
Once the composite indicator is built a number of analysis can be done to better understand the performance of its components. The “back to the detail” step suggests that the intrinsic nature of the composite indicator can give a great amount of information other than the final outcome alone.
In this view one can investigate which municipalities are the leaders and which are the laggards, make spider diagrams to show the performance of one municipality in respect to the criteria, and many other types of analysis. The methodology proposed will be then applied to the case study of Lombardy Region. The main results are reported in Sect. 4.
3 Case Study
3.1 The Evaluation Framework
According to the methodological approach described in the previous section, an evaluation framework, divided into 8 steps (Fig. 1), has been defined and applied to a pilot case study.
The analysis has focused on Lombardy Region, as it is one of the Italian regions with the highest infrastructural development (Corsi 2009).
Starting from literature review, a theoretical framework has been developed with the aim of modelling the multidimensional concept of territorial vulnerability and of defining a composite indicator. The variables have been selected from previous studies on the analysis and evaluation of territorial vulnerability (Oppio et al. 2015; Oppio and Corsi 2017), with respect to their relevance, analytical soundness and accessibility. Three main vulnerability dimensions, each divided into criteria, have been considered: the environmental, the social and the economic one. The criteria have been measured at municipality scale. Table 2 reports criteria and indicators used and the way they have been calculated.
Differently from the first efforts for measuring territorial vulnerability, this paper focus more on the methodological process than on the outputs, in order to improve the robustness and effectiveness of the Composite Territorial Vulnerability Index (CTVI). Thus, a multivariate analysis based on PCA has been perfomed for studying the overall structure of the dataset, assessing its suitability and guiding the subsequent methodological choices. Furthermore, weights have been assigned still by the use of PCA and alternative aggregation methods—linear and geometric—have been tested with reference to the theoretical framework. Finally, robustness and sensitivity analysis of the results have been developed.
In order to support decision makers in the field of infrastructures development, the CTVI has been mapped by the use of G.I.S.
3.2 Results
In order to perform robustness, uncertainty and sensitivity analysis the Monte Carlo method has been developed by generating new samples with high number of observations and simulating probability density functions similar to the ones of the existing criteria. Thus, a statistical base, that is comparable with the case under study, has been obtained. To these new samples the Equal Weights and the Weighted Sum aggregation models have been applied in order to check if we get similar results out of the simulation.
More in deep, uncertainty analysis consists in verifying the probability density functions for the two CTVI according to the largeness of the interval its values.
A first consideration is that the probability density function curves of the dependent variables as calculated on the simulated criteria are very much similar to the ones calculated on the real values. This is true both in terms of probability density function shape, as they all have a normal distribution, and in terms of interval values. A second consideration is that some grade of uncertainty exists, as the probability density function interval is quite large (Figs. 2 and 3). For understanding which criteria determine more than others the distribution of values in the probability density function, the sensitivity analysis has been carried out.
As the CTVI has been defined by supposing that a linear relation exists between the independent variable and the criteria, therefore using linear aggregation models, the sensitivity analysis has been based on the Pearson Product Moment Correlation Coefficient (PEAR) and the Standardized Regression Coefficients (SRC). The sensitivity analysis methods have been applied to the CTVI Equal Weights (CTVI_EW) and CTVI Principal Component Analysis (CTVI_PCA). According to the results shown in Figs. 4 and 5, the criteria that give a lower contribution to the territorial vulnerability evaluation are the economic ones, whilst the environmental criteria are the ones explaining most of the variance of the dependent variable.
The results of these analysis show that among the two composite indicators tested, CTVI_ EW and the CI _PCA, generate very similar outcomes, thus suggesting almost the same insights in terms of territorial vulnerability. Although the CI_PCA includes a weighting system, this does not influence the final results compared to the ones obtained by the CI_EW.
Given these premises, the linear additive model, combined to the PCA weighting system, seems to be a promising measurement of the territorial vulnerability of Lombardy region and for investigating the potential use of territorial vulnerability maps in the field of infrastructure development (Fig. 6).
4 Conclusions
The development of a composite indicator for assessing territorial vulnerability can be integrated into the regional planning system, in particular for supporting the definition of strategic socioeconomic objectives of the regional government.
The uncertainty analysis carried out allows to evaluate the range of variability of each indicator and so to estimate differences among municipalities in terms of territorial vulnerability. Moreover sensitivity analysis highlights those criteria that are significant in the definition of the composite indicator. These analyses contribute on one hand to verify the robustness of the results obtained and on the other hand to explain more in deep the topic under investigation.
The overlay of Territorial Vulnerability Composite Indicator with infrastructures plan supports effectively the feasibility studies of infrastructural development by highlighting territorial weaknesses and strengths. Furthermore, the identification of alarming situations is helpful for programming mitigation interventions.
References
Bradley M, Smith E (2004) Using science to assess environmental vulnerabilities. Environ Monit Assess 94:1–7
Corsi S (2009) Infrastrutture viarie e agricoltura. In: Agostini S, Bertoni D (eds) Per un’altra campagna. Milano, Maggioli, pp 51–59
Cutter S, Mitchell JT, Scott MS (2000) Revealing the vulnerability of people and places: a case study of Georgetown County South Carolina. Ann Assoc Am Geographers 90(4):713–737
Cutter S, Boruff B, Shirley W (2003) Social vulnerability to environmental hazards. Soc Sci Quart 84:242–261
Cutter SL, Emrich CT, Webb JJ, Morath D (2009) Social vulnerability to climate variability hazards: a review of the literature. Final Report to Oxfam America, Hazards and Vulnerability Research Institute, Department of Geography, University of South Carolina, pp 1–44
Del Giudice V, Torrieri F, De Paola P (2014) Risk analysis within feasibility studies: an application to cost-benefit analysis for the construction of a new road. Appl Mech Mater 651–653:1249–1254
Freudenberg M (2008) Composite indicators of country performance: a critical assessment. OECD, Paris
Gall M (2007) Indices of social vulnerability to natural hazards: a comparative evaluation. Doctoral Dissertation, University of South Carolina, Department of Geography, Columbia, SC
Golobič M, Breskvar Žaucery L (2010) Landscape planning and vulnerability assess-ment in the Mediterranean. Final report. Regional Activity Centre for the Priority Actions Programme
Granger K, Hayne M (eds) (2001) Natural hazards and the risks they pose to Southeast Queensland, Australian Geological Survey Organisation, Commonwealth of Australia
Kasperson RE, Kasperson JX, Dow K (2001) Vulnerability, equity, and global environmental change. In: Kasperson JX, Kasperson RE (eds) Global environmental risk, United Nations University Press and Earthscan, Tokyo, pp 247–272
Mazzocchi C, Sali G, Corsi S (2013) Land use conversion in metropolitan areas and the permanence of agriculture: sensitivity index of agricultural land (SIAL), a tool for territorial analysis. Land Use Policy 35:155–162
Menoni S, Molinari D, Parker D, Ballio F, Tapsell S (2012) Assessing multifaceted vulnerability and resilience in order to de-sign risk-mitigation strategies. Nat Hazards 64:2057–2082
Millenium Ecosystem Assessment (2005) Ecosystem and human wellbeing, Synthesis, Retrieved 10 Mar 2014 from http://www.millenniumassessment.org/documents/document.356.aspx.pdf
Munda G (2010) Social multi-criteria evaluation for a sustainable economy. Springer, Berlin
Nardo M, Saisanna M, Saltelli A, Tarantola S, Hoffman A, Giovannini E (2005) Handbook on constructing composite indicators: methodology and user guide. OECD statistic working paper. www.olis.oecd.org/2005doc.nsf/LinkTo/std-doc
OECD (2008) Handbook on constructing composite indicators. JRC European Commission
Oppio A, Corsi S (2017) Territorial vulnerability and local conflicts perspectives for waste disposals siting. A case study in Lombardy region (Italy). J Cleaner Prod 1528–1538. Doi:10.1016/j.jclepro.2016.09.203
Oppio A, Corsi S, Mattia S, Tosini A (2015) Exploring the relationship among local conflicts and territorial vulnerability: the case study of Lombardy Region. Land Use Policy 43:239–247
Oppio A, Buffoli M, Dell’Ovo M, Capolongo S (2016) Addressing decisions about new hospitals’ siting: a multidimensional evaluation approach. Ann Ist Super Sanità 52(1): 78–87
Saisana M, Saltelli A, Tarantola S (2005) Uncertainty and sensitivity analysis techniques as tools for the quality assessment of composite indicators. J R Statist Soc 168(Part 2):307–323
Saltelli A (2006) Composite Indicators between analysis and advocacy. Soc Indic Res. Doi:10.1007/s11205-006-0024-9
Saltelli A, Ratto M, Andres T, Campolongo F, Cariboni J, Gatelli D, Saisana M, Tarantola S (2008) Global sensitivity analysis: the primer. Wiley, New York
Tarantola S, Pastorelli R, Beghi MG, Bottani CE (2000) A data less pre-calibration analysis in solid state physics. In: Saltelli A, Chan K, Scott M (eds) Sensitivity analysis. Wiley, New York, pp 311–327
Tavares AO, Santos PPD (2014) Re-scaling risk governance using local appraisal and community involvement. J Risk Res 17(7):923–949. Doi:10.1080/13669877.2013.822915
Tavares AO, dos Santos PP, Paula Freirec P, Bustorff Fortu-nato A, Rilo A, Sá L (2015) Flooding hazard in the Tagus estuarine area: the challenge of scale in vulnerability assessments. Environ Sci Policy 51:238–255. Doi:10.1016/j.envsci.2015.04.010
Toro J, Duarte O, Requena I, Zamorano M (2011) Determining vulnerability importance in environmental impact assessment. The case of Colombia. Environ Impact Assess Rev 32:107–117
Torre A, Melot R, Magsi H, Bossuet L, Caron A, Darly S, Jeanneaux P, Kirat T, Pham HV (2014) Identifying and measuring land-use and proximity conflicts: methods and identification. SpringerPlus 3(1), doi:10.1186/2193-1801-3-85
Tran L, O’Neill R, Smith E (2010) Spatial pattern of environ-mental vulnerability assessment in the Mid-Atlantic region, USA. Appl Geogr 30:191–202
UNISDR (2012) Making cities resilient report 2012. My city is getting ready! A global snapshot of how local governments reduce disaster risk, 2nd edn. United Nations Office for Disaster Risk Reduction
Website References
Acknowledgement
The authors thank Andrea Biancardi for having supported the sensitivity and uncertainty analysis by the use of SimLab and Stata 13.
Author information
Authors and Affiliations
Corresponding author
Editor information
Editors and Affiliations
Rights and permissions
Copyright information
© 2017 Springer International Publishing AG
About this chapter
Cite this chapter
Oppio, A., Corsi, S., Torrieri, F., Mattia, S. (2017). Infrastructure Development and Territorial Vulnerability. The Role of Composite Indicators for Addressing Siting Decisions. In: Stanghellini, S., Morano, P., Bottero, M., Oppio, A. (eds) Appraisal: From Theory to Practice. Green Energy and Technology. Springer, Cham. https://doi.org/10.1007/978-3-319-49676-4_21
Download citation
DOI: https://doi.org/10.1007/978-3-319-49676-4_21
Published:
Publisher Name: Springer, Cham
Print ISBN: 978-3-319-49675-7
Online ISBN: 978-3-319-49676-4
eBook Packages: EnergyEnergy (R0)