Next Article in Journal
Visual Signifier for Large Multi-Touch Display to Support Interaction in a Virtual Museum Interface
Previous Article in Journal
Liquid Nanofilms’ Condensation Inside a Heat Exchanger by Mixed Convection
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Evaluation of the Sustainable Development Goals in the Diagnosis and Prediction of the Sustainability of Projects Aimed at Local Communities in Latin America and the Caribbean

by
Eduardo García Villena
1,2,*,
Alina Pascual Barrera
1,3,
Roberto Marcelo Álvarez
1,4,5,
Luís Alonso Dzul López
1,3,*,
Kilian Tutusaus Pifarré
1,4,5,
Juan Luís Vidal Mazón
1,4,6,
Yini Airet Miró Vera
1,3,5,
Santiago Brie
1,3,6 and
Miguel A. López Flores
1,3,7
1
Higher Polytechnic School, Universidad Europea del Atlántico (UNEATLANTICO), 39011 Santander, Spain
2
Department of Environment and Sustainability, Universidad Internacional Iberoamericana (UNIB), Arecibo, PR 00613, USA
3
Department of Project Management, Universidad Internacional Iberoamericana (UNINI-MX), Campeche 24560, Mexico
4
Department of Project, Universidade Internacional do Cuanza (UNIC), Barrio Kaluanda, Cuito EN 250, Angola
5
Department of Projects, Universidad Internacional Iberoamericana (UNIB), Arecibo, PR 00613, USA
6
Business Area, Fundación Universitaria Internacional de Colombia (UNINCOL), Bogotá 11001, Colombia
7
Computing Research Center, UPIICSA-Instituto Politécnico Nacional, Mexico City 07738, Mexico
*
Authors to whom correspondence should be addressed.
Appl. Sci. 2022, 12(21), 11188; https://doi.org/10.3390/app122111188
Submission received: 20 September 2022 / Revised: 29 October 2022 / Accepted: 31 October 2022 / Published: 4 November 2022
(This article belongs to the Special Issue Engineering Applied to Sustainable Development Goals II)

Abstract

:
The purpose of this article is to help to bridge the gap between sustainability and its application to project management by developing a methodology based on artificial intelligence to diagnose, classify, and forecast the level of sustainability of a sample of 186 projects aimed at local communities in Latin American and Caribbean countries. First, the compliance evaluation with the Sustainable Development Goals (SDGs) within the framework of the 2030 Agenda served to diagnose and determine, through fuzzy sets, a global sustainability index for the sample, resulting in a value of 0.638, in accordance with the overall average for the region. Probabilistic predictions were then made on the sustainability of the projects using a series of supervised learning classifiers (SVM, Random Forest, AdaBoost, KNN, etc.), with the SMOTE resampling technique, which provided a significant improvement toward the results of the different metrics of the base models. In this context, the Support Vector Machine (SVM) + SMOTE was the best classification algorithm, with accuracy of 0.92. Lastly, the extrapolation of this methodology is to be expected toward other realities and local circumstances, contributing to the fulfillment of the SDGs and the development of individual and collective capacities through the management and direction of projects.

1. Introduction

1.1. Sustainable Project Management

The concept of sustainable development appeared for the first time in 1987, following the publication of the United Nations Brundtland Report, which, among other issues, denounced the environmental impacts derived from the intensive use of natural resources in production activities [1].
The social policies and movements of the late 20th century led the term to acquire an economic dimension, beyond the purely environmental one, converging with the postulates of Corporate Social Responsibility (CSR), aimed at assessing the impact of business actions on society.
This meta-concept, called sustainability or the “Triple Bottom Line (TBL)”, evaluates the creation of value in companies, distinguishing between the economic, social, and environmental spheres in their income statements [2].
The current paradigm shift represented by sustainability involves moving away from the here and now of CSR and evolving towards new models that last over time [3], which can be part of the strategic and operational processes of organizations through projects [4]. In this way, projects become a potential means of transmitting sustainable practices to local communities [5], promoting behavioral changes and delivering business value [6].
However, even though, in recent years, there has been an effort to incorporate sustainability in a cross-cutting manner into project management [7], there is a gap between the perception of the importance of sustainability and its actual use in project management practice [8].
According to Okland [9], one of the reasons stems from the ambiguity of the term and its multiple definitions, which cause confusion when applying it to project management, making the acquisition of competencies in this area essential for the project manager (Table 1).
A significant example is the scarcity of sustainable criteria contained in the currently most accepted project norms and standards, such as IPMA ICB4® [10], PMBOK® [11], PRINCE2® [12], or the Guide for Project Management ISO 21500:2012 [8,13,14,15]. In this context, a sustainable approach is only seen in agile project methodologies, aimed at software development (Agile Methodologies), and in the PRISM methodology (Projects Integrating Sustainable Methods), which incorporates governance, environmental, economic, social, and technical factors from a set of good practices collected in different ISO standards [16].
On the other hand, both the PMBOK® Guides and ISO 21500:2012 continue to consider project management from a utilitarian view, i.e., focused exclusively on the outcome of the actions and, therefore, on the benefits of the project [9]. Along the same lines, Jeans et al. [17] allude to training to eradicate the dissonance implied by utilitarianism, in which the benefits resulting from the project are obtained only at the time of its execution [18], thus avoiding the durability over time of its actions. This perception of project management limits the introduction of sustainable criteria from very early stages, causing a misalignment from the point of view of local community stakeholders [19].
In this sense, because the effects of a project can last much longer than the project itself [9], sustainability in project management requires a governance framework—public or private—that is holistic and, therefore, focused on the early stages of project development, prior to making important decisions.
In short, there is no doubt about the importance of projects as an engine of change and a driving force for the development of local communities’ capacities for the creation of sustainable value. However, the current utilitarian conception of the term, reflected in the economic instrumentalization and the gaps in norms and standards, envisions sustainability as an axiom that does not last throughout its life cycle.
It is therefore necessary to abandon non-holistic approaches and reduce the disconnection between sustainability and project management practices on local communities [20] to create the necessary conditions and develop the capacities of individuals through project management norms and standards.

1.2. Sustainability Evaluation Models in Project Management

Over the last two decades, numerous sustainability assessment models applied to project management have been developed [8]. Some of these models, such as those of Araujo [21], Macaskill and Guthrie [22], and Corder et al. [23], maintain a holistic view and incorporate sustainability within the project management process. However, other models, such as that of the OECD [24], conceive it as an outcome [9].
In any case, it is common in these models for the measurement to incorporate certain evaluation criteria beyond the traditional ones (scope, time, and cost), which use indicators of all kinds. For example, the OECD model employs criteria such as efficiency, effectiveness, impact, relevance, and sustainability, which use economic, environmental, social, and technological indicators in a cross-cutting manner, among others [9].
However, the models are scattered and, in general, incomplete, without a defined instrumentalization, making it very difficult to integrate them with the organization’s idiosyncrasy and, consequently, taking advantage of the competitive edge in the market.
Using a quantitative method of priority scales based on expert judgement (AHP method), Martens and Carvalho [8], aware of this problem, identified and condensed the variables of the main sustainability models focused on TBL in the context of the management and success of projects in different areas of engineering and administration.
Table 2 shows the most highly valued indicators according to expert judgement and grouped by dimension.
Within the scope of this research, a model based on the Sustainable Development Goals (SDGs) was proposed to assess the sustainability of multi-sectorial projects. As we will see in the following section, no general sustainability assessment models incorporating the SDGs in project management have been found, except for isolated cases aimed at a specific sector.
In this context, the SDGs play a very important role in developing capacities at the local community level and breaking the traditional paradigm, by influencing issues such as gender perspectives, inequality reduction, and climate action, among others [25,26].

1.3. Sustainable Development Goals (SDGs) and Their Relation to Project Management

The Sustainable Development Goals (SDGs) were presented for the first time in 2015, during the United Nations Sustainable Development Summit, as the International Community’s response to the challenges of climate change and sustainable development (Table 3). These 17 goals, to be achieved by all nations belonging to the UN General Assembly before 2030, are composed of a total of 169 targets and 232 indicators, supervised by a team of experts who report the data to a publicly accessible repository for the follow-up and monitoring of their implementation [20].
In contrast to sustainable project management, the relationship between the SDGs and project success is a topic that has been rarely addressed in the literature [27]. Some authors allude to the lack of maturity of organizations in reflecting the impacts of the SDGs in their reporting [28], which in turn produces a knowledge gap, preventing the dissemination of project successes or failures [9].
An example that perfectly illustrates the challenge for project managers to include the SDGs in the project life cycle is the climate change phenomenon, which directly affects, to a greater or lesser extent, each of these goals [29].
In April 2022, the Intergovernmental Panel on Climate Change (IPCC) published the third mitigation part of its Sixth Assessment Report. One of the conclusions of this report was that, even though great efforts have been made in the last decade to reduce mitigation costs, especially for solar energy, there is still a considerable gap between current measurements and those needed to limit warming to 1.5 °C by 2030 [9,30].
This discrepancy with respect to national and global mitigation targets poses a challenge for project managers seeking to measure the impact of the SDGs, as it is very common for aspects such as time, cost, and quality to be highlighted, with less consideration being given to the environmental, social, and financial effects of the TBL.
In this sense, the influence of the financial factor in general and the proliferation of economic models and accounting tools of all kinds has added further confusion in assessing the impacts of the SDGs, thus compromising project success [31].
Despite this, there are initiatives by different countries, institutions, and non-governmental organizations toward developing strategies to align their projects with the SDGs. For example, the Government of Canada, through different universities such as Waterloo, Vancouver Island University, Laval, and other organizations, successfully funds projects based on the SDGs in local communities, provinces, and the private sector, among others [32]; the University of Newcastle (Australia) periodically issues reports on its activity in projects related to climate change, water purification, gender equality, non-poverty, etc. [33]; the Asia Society provides templates aimed at students where the schedule, program, objectives, expectations, tools, etc., are defined to incorporate the SDGs into projects [34]; Google Developer Student Clubs invites students to create projects that contribute in solving one or more of the SDGs, using Google technologies [35], etc.

1.4. Sustainability Ranking in Latin America and the Caribbean

To disseminate the repository, reports are periodically issued to show the world ranking compliance with the SDGs according to different countries.
In this regard, the average SDG index in Latin America and the Caribbean stood at a discreet 69.04/100 in 2022, with a general trend towards stagnation in the coming years [36].
Figure 1 shows the progress in meeting the SDGs for selected countries in Latin America and the Caribbean since 2015 and up to 2022.
We can see that Chile, Uruguay, and Cuba are the three countries leading in the SDG compliance ranking, while Venezuela and, especially, Haiti occupy the last positions.

1.5. Project Selection and Classification

A total of 186 projects from Latin America (80.6%) and the Caribbean (19.4%) were selected and classified in this research article, covering a wide variety of aspects from service provision (30%), business creation (23%), building design, extensions, and refurbishments (19%), process redefinition (11%), product design and development (9%), and, lastly, people training (8%).
The selection included a grouping of the projects by dimension as a preliminary step toward a hierarchical ranking of sustainability, in reference to compliance with the SDGs (Table 4).
As shown in Table 4, achieving sustainable development requires the participation of all actors in society, including local communities, which take a leading role in project management [39,40].

1.6. Artificial Intelligence and Sustainability

Artificial intelligence (AI) can be defined as software technology that encompasses one or more capabilities referring to perception, prediction, classification, decision making, diagnosis, and logical reasoning, among others [39].
This technology is fully compatible in complying with the SDGs, as stated annually in the summits organized by the International Telecommunication Union [41] in partnership with several entities and more than 35 UN agencies.
In successive meetings held periodically, the need for AI to accelerate compliance with the UN’s SDGs is emphasized through the presentation of different projects aimed at this end [42].
Table 5 shows some of these activities. We can see that they refer to a wide variety of multidisciplinary sectors in the social, economic, and environmental fields.
On the other hand, a November 2018 McKinsey Global Institute study identified as many as 135 initiatives out of a possible 156 that fully or partially linked AI to one or more of the SDGs [38].
Figure 2 illustrates that most of these initiatives were related to Goals 3, “Good health and well-being”, and 16, “Peace, justice, and strong institutions”.

1.7. Machine Learning and Unbalanced Classes

Within the context of AI, machine learning constitutes a new paradigm integral to data mining techniques [43] that, among other functions, enables developing a predictive model with a large amount of data that can result in a numerical value (regression) or label a category of data (classification).
Depending on the type of output and processing approach, machine learning can be presented with examples of inputs and observed outputs (labels or targets), where the objective is that the model trains with this data set and learns to define a general rule that assigns the appropriate output label to a new value [44,45]. This type of classification, called supervised learning, is the one addressed in this research paper.
However, it is common for the metrics provided by the classifiers (their accuracy in particular) to be affected by classification problems of the variable to be predicted, where there is a class described as the majority that agglutinates a large proportion of the data, and other minority classes, poorly represented in terms of information. In this type of situation of unbalanced classes, it is common to resort to oversampling techniques, where the minority class is artificially increased (SMOTE).

1.8. Research Design

As we have seen, the few references that relate project management to the SDGs are aimed at very specific sectors and, at best, involve a few targets. Likewise, no literature on machine learning has been found either, which would help in reducing the existing gap between both concepts. The non-holistic conception prevailing in most of the projects also represents a problem for maintaining sustainability once the project has been implemented.
Having stated the problem of resistance to paradigm shifts in sustainable project management and leadership through AI, thus influencing the strategic objectives of the organization [46,47], the research question posed was as follows:
Is it possible to help bridge the gap between sustainability and project management by developing a holistic model based on machine learning, using the Sustainable Development Goals as input parameters to classify and forecast multi-sectorial projects according to their level of sustainability?
In this context, the guidelines followed in this research are shown in Table 6.
The research sub-questions were as follows:
  • Why is it necessary to consider the Sustainable Development Goals to assess the sustainability of projects?
  • Is it possible to develop the capabilities of a project manager within sustainable development terms?
  • How can artificial intelligence break the current paradigm of sustainability through the Sustainable Development Goals?
The research was an objective type since, from the ontological point of view, it was assumed that the unit of observation—in this case, the answers to the Likert-scale questionnaires administered to expert panels—had its own identity constitution [49], while the authors of this research, as independent observers in reference to the nature of knowledge (epistemology), limited themselves in representing such reality with precision and accuracy [48].

2. Materials and Methods

The methodology followed in this research was descriptive and relational, quantitative, non-experimental, and transactional, because no hypotheses were proposed and no variable was manipulated, but it “[...] measured, evaluated, or collected data on various aspects, dimensions, or components of the phenomenon to investigate [in their natural work environment and in a single time]” [50,51].
As can be seen from the objective guiding this research work, the methodological scope comprised, broadly speaking, several distinct stages: first, a Likert-scale questionnaire based on the SDGs was prepared and provided to a group of experts for them to evaluate, on a scale of 1 to 5, the level of sustainability of 186 projects focused on local communities in various countries of Latin America and the Caribbean; second, the level of consensus among the group of experts and a global index of sustainability of the sample were determined using the Fuzzy Logic Designer tool of the Matlab R2021b mathematical software®; third, the classes of high, medium, and low were defined for the sustainability of the projects; fourth, the synthetic minority over-sampling technique (SMOTE) was included during the training phase of several supervised learning classifiers (Logistic Regression, K-Nearest Neighbors, Support Vector Machine, AdaBoost, Gaussian Process Classifier, and Random Forest), using the Scikit Learn library of Python 3.10. Lastly, the different resulting models were tested, and the one that offered the best accuracy for sustainability forecasting in future projects was chosen.
The panel of experts for evaluating the sustainability of the projects was composed of five groups of teachers and third-party professionals from the postgraduate course in design, management, and project management of the European University of the Atlantic (UNEATLANTICO), who previously established common guidelines toward achieving a good level of consensus.

2.1. Population and Sample

Initially, the study population consisted of a total of 210 international cooperation projects, targeting local communities in Latin American and Caribbean countries. To determine the necessary sample size, and given that the intention was to estimate percentage distributions of qualitative variables in the statistical calculations, Equation (1) for finite populations was used [52]:
n N Z 1 α 2 2 p q N 1 ε 2 + Z 1 α 2 2 p q
where:
  • n = required sample size;
  • N = population size;
  • Z1−α/2 = 1.96 (Z-statistic, calculated at 95% confidence level);
  • p = q = 0.5 (typical values under worst-case conditions);
  • Error ( ε ) = 0.05.
The sampling was convenience sampling—that is, non-probabilistic.
Substituting the values into the formula resulted in a required sample size for the study of n 136 .

2.2. Data Collection

As mentioned, the research instrument consisted of a Likert-scale questionnaire, which collected a total of 17 measurement criteria or items corresponding to each of the SDGs.
The scale categories were as follows: “1—Insignificant (I)”; “2—Not So Significant (NSS)”; “3—Significant (S)”; “4—Very Significant (VS)”; “5—The Most Significant (TMS)”.
The information was collected between the dates of 1 January 2010 and 31 December 2019. A total of 210 projects were evaluated during this time, of which 24 were discarded due to deficiencies in the process.

2.3. Assessment of the SDG Indicators

The valuation method of the SDG indicators in the projects was inspired by the Sustainability Barometer, defined by the World Conservation Union [53].
The idea is that an objective, with a major environmental component—such as the purification of waste effluents—should not be achieved at any cost, but should maintain a balance with the other economic and social dimensions.
As illustrated in Figure 3, ecosystem well-being is located on the x-axis and socio-economic well-being on the y-axis. The intersection of the two provides a reading of the overall sustainability of the indicator, with the caveat that a low result on one axis cancels out the result on the other, with the more conservative approach prevailing in the final decision.
Figure 4 illustrates the main indicators of the SDGs, which were subsequently used by the experts in assessing the scale categories according to the Sustainability Barometer technique.

2.4. Project Distributions among the Expert Panel

Project distributions among the expert groups was randomized, as illustrated in Table 7.
After verifying the validity and reliability of the proposed measuring instrument by means of Cronbach’s Alpha statistic, an analysis of variance (ANOVA) was performed to determine whether there were significant differences between the groups’ means or whether these were due exclusively to chance. To this end, data independence, normality, and homoscedasticity were tested. Both tests were performed using SPSS version 26 statistical software.

2.5. Data Preparation

Data preparation consisted of eliminating duplicate records or records with outliers, empty fields, etc.

2.6. Measurement of Expert Consensus

Consensus is defined as an opinion or position reached by a group of people as a general agreement [54].
As shown in Equation (2), consensus is a measure of attraction to a mean value:
Cns X = 1 + i = 1 n p i · log 2 1 X i μ x d x
where:
  • X= list of categories (“1—Insignificant (I)”...“5—The Most Significant (TMS)”);
  • pi = probability of each X;
  • dx = Xmax -Xmin;
  • Xi = particular element of X;
  • μ x = mean or expected value;
It is, therefore, a measure of dispersion for ordinal data in the interval [0, 1] and which, on a Likert scale with gradation between responses, can be transformed into the form of percentage agreement [55], as shown in Table 8.

2.7. Categorization of Project Level of Sustainability

Each of the projects was then categorized into three classes (high, medium, low) according to their level of sustainability. To this end, a new variable, “Level of Sustainability”, was created, containing the sum of the corresponding objective ratings for each of the projects ( x ¯ = 69.75; s = 7.868).
Equation (3) below and Figure 5 provide the two cut-off points for defining the class categories:
x ¯ 0.75 · s   Cut-off points

2.8. Determination of a Global Sustainability Index for the Project Sample

The determination of the overall sustainability index of the sample was carried out using the fuzzy classifier incorporated in Matlab R2021b®. The input variables were, separately, the mean of the consensus corresponding to each of the dimensions, and the joint sustainability index obtained as an output variable in a gradation of five scales between the “very low” to “very high” linguistic variables.
The Mandani procedure [57] and triangular membership functions were used for their simplicity, functionality, and invariance for each score, which facilitated computational calculation at the intersections [58]. In this case, 33 fuzzy rules, obtained through expert judgment, were used.

2.9. Types of Classifiers

Table 9 shows the classifiers included in the Scikit Learn library of Python 3.10 and used in this research work.

2.10. Data Resampling Techniques (SMOTE)

Data resampling techniques such as SMOTE achieve uniform distribution among unbalanced classes by altering the data distribution of the model. In this sense, the SMOTE algorithm, based on the K-Nearest-Neighbors classifier, served to create new instances within the minority classes [59,60].

2.11. Choice of the Best Classification Model

The stages implemented using the Scikit Learn library of Python 3.10 were the following:
  • Data preparation and pre-processing;
  • Data analysis and exploration;
  • Assignment of the characteristic’s matrix and the vector of classes or target;
  • Codification of the vector of classes or target in dummy variables;
  • Division of the data into training (80%) and testing (20%), with stratification of the output variable, to ensure homogeneity in the representativeness of the data in both groups.
  • Training phase:
  • Evaluation of the benchmark strategy with DummyClassifier.
  • Elaboration of a pipeline containing the SMOTE oversampling technique, the scaling or normalization of the data, and the corresponding classifier.
  • Use of the RepeatedStratifiedKFold cross-validation technique to minimize data overfitting.
  • Use of the GridSearchCV technique to search for the best parameters.
  • Testing phase:
  • Model test with records not used during training (without SMOTE).
  • Determination of metrics and choice of the model with the best accuracy.
  • Printout of results.

2.12. Performance Evaluation Metrics

Table 10 shows the metrics used in this research paper.

3. Results

3.1. Differences between Groups of Experts (ANOVA)

The analysis of variance to test whether there were differences between the means of the groups of experts resulted in compliance with the requirement of independence and Levene’s test for homoscedasticity (constant variances), as each project was treated independently and provided a p-value of 0.6924 > 0.05, respectively. However, the Kolmogorov–Smirnov test resulted in a p-value < 0.0001, which, being less than 0.05, rejected the null hypothesis of normal data distribution, so that the data did not follow a normal distribution.
ANOVA is quite robust in the absence of normality, especially if the groups have a very similar size, as is the case; therefore, we can conclude that the means of the different groups being equal were accepted, and that the differences between groups were due exclusively to chance.

3.2. Validation and Reliability of the Measuring Instrument

Validation of the measurement instrument was based on the relevance, pertinence, and clarity of each of the 17 SDGs by a panel of experts [52].
Reliability was determined by means of Cronbach’s Alpha statistic, and it included the set of objectives associated with sustainability.
The value of Cronbach’s Alpha was 0.865, which is considered good data for the internal consistency of the instrument [61]. Among other aspects, this indicator ensures that the evaluation was not left to chance, so the study can proceed.
Table 11 shows the statistics associated with Cronbach’s Alpha. The minimum value is 0.852, and the elimination of item 2 would improve the result (from 0.865 to 0.867). However, this small statistical improvement does not compensate for the loss of information due to the exclusion of the item, so it was decided to retain it.

3.3. Consensus Measures

To determine consensus, the SDGs were grouped into three dimensions in this research, namely environmental, social, and economic, so that the same target could refer to multiple dimensions [62].
As shown in Table 12, a moderate consensus was obtained (see Table 8), with low levels of dispersion with respect to the weighted mean, demonstrating its reliability.
In this sense, the SDGs that obtained the highest consensus were Goal 2, “Zero hunger”, with 79.87%, and Goal 6, “Clean water and sanitation”, with 76.10%. Goal 14, “Life below water”, obtained the lowest consensus, with 63.38%.

3.4. Sustainability Level of the Project Sample

As a result of the classification, a typical situation of unbalanced data could be seen, where the majority class (medium) accounted for 60.2% of the projects, far behind the low and high classes, with 21.5% and 18.3%, respectively (Table 13).

3.5. Determination of the Global Sustainability Index for Projects

The overall sustainability index for the projects was 0.638, as illustrated in Figure 6.

3.6. Accuracy Metric Threshold Determination

The DummyClassifier (DMC) classifier determined a threshold of 0.608 ± 0.01 for the accuracy metric, which also corresponds to the probability of finding a majority class 2 element within the training set (90 possible cases/148 total cases). This means that any model with an accuracy value below this threshold should be discarded.

3.7. Base Model Metrics

Figure 7 illustrates a comparative picture of the overall accuracy metric for the different classifiers implemented in the base model (unbalanced) during the training phase.
The best classifiers are in the following order: SVM   0.906 ± 0.047 ;   KNN 0.897 ± 0.057 ;   LR 0.872 ± 0.045 ;   RF 0.861 ± 0.069 .
We can see that, in most of the classifiers, both the mean and the median are very close together, suggesting a certain symmetry and stability of the indicator distribution.
However, for unbalanced data, conclusions cannot be drawn from the overall accuracy metric alone [63,64], as it may not be considering the minority classes; therefore, in these circumstances, we must look for other types of metrics that can provide greater reliability in the interpretation of the indicators.
Table 14 shows the metrics obtained in the testing phase for the best classifiers. As can be seen, the order of importance of the classifiers is the same as that obtained during the training phase. It can be observed that the accuracy values achieved for each particular class are quite good.
In general, high values of precision and recall were obtained, indicating that the model generalizes said class perfectly. However, for the Random Forest model, maximum precision and low recall were obtained for the low class, suggesting that this model does not detect said class well, but, when it does, it is highly reliable.

3.8. Balanced Model Metrics

Similarly, Figure 8 illustrates the comparison of the overall accuracy metric for the different classifiers implemented in the balanced model with SMOTE, during the training phase.
We can see how the improvement in this metric is significant when oversampling in three of the classifiers: GAUSS 0.948 ± 0.036 ;   SVM   0.926 ± 0.033 ;   LR 0.895 ± 0.041 . Meanwhile, for KNN 0.874 ± 0.057   and   RF 0.859 ± 0.065 , it worsens slightly.
Table 15 shows the metrics obtained during the testing phase for the best classifiers with oversampling. As can be seen, the best classifier is SVM, with overall accuracy of 0.92, similar to that obtained during the training phase, which, as in the case of the LR and KNN classifiers, suggests the good generalization of the model. In the case of the GAUSS classifier, a value of 0.87 << 0.94 is obtained, indicating probable overfitting.

4. Discussion

To help to bridge the gap between sustainability and project management, a methodology based on the SDGs was developed to assess sustainability in a sample of multi-sectoral projects in the Latin American and Caribbean region. This is important because, while there are numerous models that relate project management to sustainability in specific sectors, there are few that involve the SDGs in the creation of shared value. In this sense, [27] highlight the role of project managers in taking a leading role in the creation of a conceptual framework to measure the impacts of the SDGs on projects through the lens of TBL. However, the acquisition of competencies and tools is not always the most appropriate, meaning that solutions to problems are sought based on the immediacy and benefit of the results, instead of developing strategies that involve the entire project development process. Along the same lines, [65] and [66] consider that the SDGs should be deemed as key inputs to the business strategy and not as an additional external cost to the company, integrating them into the project life cycle. On the opposite side, other authors question the ability of the SDGs to determine project success. For example, [67] base their analysis on urban indicators and justify their argument by the variability and complexity of their definition; the political nature of the data; the scarce availability of standardized, open, and comparable data; the lack of solid institutions for data collection and monitoring; and, lastly, the difficulty of their application toward different local communities. Along the same lines, [68] provide a more environmentalist view and justify their argument in the proliferation of undefined and unmeasurable ideals, with the approach ambiguity of the SDGs 14 and 15 as an example.
Artificial intelligence was used in this research article to diagnose, classify, and predict the sustainability of a sample of projects aimed at local communities in Latin America and the Caribbean, using the fulfillment of the SDGs as a reference.
In the literature, we found experiences of classification and the classification of projects in relation to their degree of complexity [69], strategies [70], construction and sustainable infrastructure [71], and leadership styles [72], among others; however, we found no precedents for the classification of projects based on machine learning that took into account the level of compliance with the SDGs in local communities in Latin America and the Caribbean.
In reference to the diagnosis of the sustainability scope, Latin America and the Caribbean recorded a discreet value of 69.04/100 until the year 2022—that is, an advance of only 1.19% compared to 2015 [36] and three points above the value of the world average index of 66 for the same year.
This figure, compounded by the pandemic caused by SARS-CoV-2, means that progress is not being made at an adequate pace to meet the 2030 Agenda [73]. In this context, the worst-performing SDGs in the region were 10—Reduced inequalities; 9—Industry, innovation, and infrastructure; and 16—Peace, justice, and strong institutions [36].
Indeed, aspects such as the quality and equity of Internet access, economic slowdown, inequality, wage and gender gaps, and the fight against corruption, among others, are the major challenges currently facing the region [22,74]. In this context, we believe that project management and leadership is an excellent opportunity toward addressing the challenges posed by these objectives and, thus, implementing good practices in local communities in Latin America and the Caribbean.
During the course of the research, we saw that AI technology is closely linked to the fulfilment of the SDGs. In this regard, AI’s relevance to the SDGs was noted in numerous summits organized by the International Telecommunication Union (ITU) under the auspices of the United Nations, from which a large number of initiatives and projects have emerged [42]. Many of them are related to goals 3, Good health and well-being, and 16, Peace, justice, and strong institutions [38]. This means that there is a special consideration in AI for issues that affect health and governance—for example, in Latin America and the Caribbean, in relation to HIV infections, quality of healthcare services, teenage pregnancies, communicable and emerging diseases such as cholera, dengue, zika virus, COVID-19, among others. These results are corroborated by authors such as Vinuesa et al. [75], who believe that AI can facilitate 80% of the fulfillment of the SDGs; however, it can also constitute a constraint due to the price of the technology. In this context, we consider that AI is necessary for the fulfilment of the SDGSs, but always adopting compromising solutions between the cost of the technology and the benefits derived from its implementation, which is, in turn, the foundation of the concept of sustainable development [76,77].
When determining the overall sustainability level of the project samples, very similar consensus values were obtained between the groups of experts and dimensions: Environment (71.6), Social (71.8), and Economic (71.5). There were no significant differences between the expert panels, by which the variations between group averages were attributable to chance. These consensuses averaged an overall mean rating of 0.638 on a fuzzy set system corresponding to a medium level of sustainability. These data are a true reflection of the compliance of the SDGs in Latin America and the Caribbean to date, since, as we have seen, the SDG Index is also within an equivalent position in the region [36], which confirms the model’s robustness. This procedure is corroborated by Encarnacion [55], who, in his research, uses, as parameters of the input variable, the consensuses calculated as a measure of dispersion for ordinal category data. In this sense, the consensuses presented a low level of dispersion in general, which ratified the consistency of the weighted mean.
Prior to the model training phase, the sample of projects was categorized according to their level of sustainability. This classification resulted in the following percentages: high (18.3%), medium (60.2%), and low (21.5%). These provided the desired values or targets for supervised learning. We can see that most of the sample presented a medium level of sustainability, which is consistent with the result obtained through the fuzzy set system.
In reference to finding the best model for predicting sustainability in projects aimed at local communities in Latin America and the Caribbean, the Gaussian Process Classifier was found to have a very good fit during the training phase (0.948); however, accuracy dropped significantly during the training phase (0.87), indicating the possibility of overfitting. This is because the use of resampling techniques such as SMOTE can introduce examples from the minority classes into the majority class and cause, in practice, problems of overfitting or underfitting, which could invalidate the model [78].
Lastly, the SVM + SMOTE classifier was the one that obtained the best level of accuracy, both globally (0.92) and individually (H: 0.95; M: 0.97; L: 0.92), for each of the classes, superior to the rest of the classifiers during the testing phase. These metrics were quite similar to those obtained during the training phase, which indicates the good generalization of the model, i.e., no overfitting. These results are consistent with those found by Demidova and Klyueva [79], where it is concluded that the SMOTE algorithm significantly improves the metrics of the SVM classifier, even with very unbalanced data.

5. Conclusions

This research article has tried to develop a methodology based on guaranteeing project sustainability from a holistic perspective, abandoning the CSR approach, and adopting sustainable criteria beyond the triangular relationship (time, cost, and scope) of the traditional project manager’s vision.
In this sense, the analysis of the literature review on sustainability and project management revealed that:
  • There was a gap between sustainability and its application to project management;
  • the integration of sustainability should take place throughout the entire project life cycle and not only focus on the outcome; and,
  • the sustainability assessment of the project should consider a set of targets and indicators based on TBL.
Although the integration of sustainability into the project life cycle process is beyond the scope of this research, it is appropriate to mention the need for establishing a new paradigm to help to bridge the gap between the perception of sustainability—and the SDGs—and its application to project management.
In this way, an affirmative answer to the research question was provided by developing a machine learning model to classify and evaluate project sustainability. In this regard, the result showed that the classifier (SVM + SMOTE) was the best option, with overall accuracy of 0.92, suggesting the good generalization of the model.
Therefore, artificial intelligence is an innovative tool for bringing the SDGs closer to managing projects aimed at local communities, particularly in Latin America and the Caribbean. The model can be used, in this case, to identify negative externalities and inefficiencies in projects and adopt the corresponding internalization measures—for example in the areas of greatest concern within the region, such as social inequalities, pollution, and corruption or discriminatory laws.
On the other hand, although this is a contentious aspect, the use of the SDGs as independent variables of the model simplifies and organizes the targets and indicators, providing a framework for the feasibility of measuring project sustainability. With this relating to another of the research sub-questions, it was shown that, given the existing confusion between the terms and definitions of sustainability and its application in project management, training the project manager in general, and particularly in the field of the SDGs, is essential in extending the benefits of the results beyond the early stages of project implementation.
Lastly, the methodology followed in this research and the approach to measuring the SDGs can link the results obtained in the projects to improve the national and global indices of the region.

6. Recommendations

In the future, this research can be improved by expanding the sample of projects and their characteristics to other communities different from Latin America and the Caribbean. A neural network model with SMOTE could also be included, and even other techniques that do not alter the data distribution, such as adjusting the optimal prediction probability threshold or the hyperparameter penalty, which could be tested.

7. Limitations

The main limitations of the methodology described in this research article are based on the difficulty in establishing a well-defined conceptual framework, given the differences between the global definitions of the SDGs’ objectives and their application at the project management level [65]. This means that, sometimes, for a specific sector, the model does not cover all the necessary indicators.

Author Contributions

Conceptualization, A.P.B. and R.M.Á.; Data curation, A.P.B. and E.G.V.; Formal analysis, L.A.D.L.; Investigation, R.M.Á. and S.B.; Methodology, E.G.V. and Y.A.M.V.; Project administration, J.L.V.M. and S.B.; Resources, L.A.D.L. and R.M.Á.; Software, K.T.P.; Supervision, E.G.V.; Validation, K.T.P. and M.A.L.F.; Visualization, A.P.B. and M.A.L.F.; Writing—original draft, E.G.V.; Writing—review and editing, E.G.V. and Y.A.M.V. All authors have read and agreed to the published version of the manuscript.

Funding

This research is part of European Project Erasmus + Lovedistance (Reference: 609949-EPP-1-2019-1-PTEPPKA2-CBHE-JP), funded by the EACEA (Education, Audiovisual and Culture Executive Agency), European Commission.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Informed consent was obtained from all subjects involved in the study.

Data Availability Statement

The data presented in this study are available on request from the corresponding author. The data are not publicly available due to the conditions of the project contract with the funder (Society for Regional Development of Cantabria).

Acknowledgments

The authors would like to thank the Cantabria Center for Industrial Research and Technology (CITICAN, Centro de Investigación y Tecnología Industrial de Cantabria) and the Universidad Europea del Atlántico for their valuable collaboration.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Brundtland, G.H. Our Common Future: Report of the World Commission on Environment and Development. Geneva, UN-Dokument A/42/427. 1987. Available online: http://www.un-documents.net/ocf-ov.htm (accessed on 16 August 2022).
  2. Elkington, J. Cannibals with Forks: The Triple Bottom Line of 21st Century Business; Capstone: Oxford, UK, 1998. [Google Scholar]
  3. United Nations. Claves Empresariales de la Nueva Estrategia de Desarrollo 2030. 2021. Available online: https://www.agenda2030.gob.es/recursos/docs/informe-progreso21-eds-2030.pdf (accessed on 17 August 2022).
  4. Obradović, V. Model Upravljanja Promenama primenom Metodologije Projektnog Menadžmenta. Ph.D. Thesis, Faculty of Organizational Sciences, University of Belgrade, Belgrade, Serbia, 2010. [Google Scholar]
  5. Goel, A.; Ganesh, L.S.; Kaur, A. Sustainability integration in the management of construction projects: A morphological analysis of over two decades’ research literature. J. Clean. Prod. 2019, 236, 117676. [Google Scholar] [CrossRef]
  6. Project Management Institute. A Guide to the Project Management Body of Knowledge (PMBOK® Guide), 7th ed.; PMI: Newton Square, PA, USA, 2021. [Google Scholar]
  7. Brones, F.A.; Carvalho, M.M. From 50 to 1: Integrating literature toward a systemic ecodesign model. J. Clean. Prod. 2015, 96, 44–57. [Google Scholar] [CrossRef]
  8. Martens, M.L.; Carvalho, M.M. Sustainability and Success Variables in the Project Management Context: An Expert Panel. Proj. Manag. J. 2017, 47, 24–43. [Google Scholar] [CrossRef]
  9. Okland, A. Gap Analysis for Incorporating Sustainability in Project Management. Procedia Comput. Sci. 2015, 64, 103–109. [Google Scholar] [CrossRef] [Green Version]
  10. International Project Management Association. ICB—IPMA Competence Baseline, Version 4.0; International Project Management Association: Nijkerk, The Netherland, 2015. [Google Scholar]
  11. Project Management Institute. A Guide to the Project Management Body of Knowledge (PMBOK®Guide), 6th ed.; PMI: Newton Square, PA, USA, 2017. [Google Scholar]
  12. PRINCE2® Agile, Successfully Deliver Projects Using Agile Techniques. Available online: https://www.axelos.com/certifications/propath/prince2-agile-project-management (accessed on 15 September 2022).
  13. International Organization of Standardization. Orientación Sobre Gestión de Proyectos ISO 21500; International Organization of Standardization: Geneva, Switzerland, 2012. [Google Scholar]
  14. Paneque, A.; Bastante, M.J.; Capuz, S. Analysis of aspects and principles related to sustainability in IPMA ICB4. In Proceedings of the 21th International Congress on Project Management and Engineering, Cádiz, Spain, 12–17 July 2017. [Google Scholar]
  15. Eskerod, P.; Huemann, M. Sustainable development and project stakeholder management: What standards say. Int. J. Manag. Proj. Bus. 2013, 6, 36–50. [Google Scholar] [CrossRef]
  16. Padickakudy, M. Sustainability in the Project Management Process. Master’s Thesis, Coventry University, Coventry, UK, 2019. [Google Scholar]
  17. Jeans, H.; Thomas, S.; Castillo, G. The Future is a Choice: The Oxfam Framework and Guidance for Resilient Development; Oxfam International: Oxford, UK, 2016; Available online: https://oxfamilibrary.openrepository.com/bitstream/handle/10546/604990/ml-resilience-framework-guide-120416-en.pdf?sequence=1 (accessed on 15 September 2022).
  18. Raufflet, E.; Barin-Cruz, L.; Brès, L. An assessment of corporate social responsibility practices in the mining and oil and gas industries. J. Clean. Prod. 2014, 84, 256–270. [Google Scholar] [CrossRef]
  19. Baba, S.; Mohammad, S.; Young, C. Managing project sustainability in the extractive industries: Towards a reciprocity framework for community engagement. Int. J. Proj. Manag. 2021, 39, 887–901. [Google Scholar] [CrossRef]
  20. United Nations. Global SDG Indicators Database. 2021. Available online: https://unstats.un.org/sdgs/unsdg (accessed on 15 September 2022).
  21. Araújo, J.B. Development of evaluation method of performance manufacturing process considering sustainability parameters. Doctoral Thesis, Engineering School of São Carlos, University of São Paulo, São Carlos, Brazil, 2010. [Google Scholar]
  22. Macaskill, K.; Guthrie, P. Risk-based approaches to sustainability in civil engineering. Eng. Sustain. 2013, 166, 181–190. [Google Scholar] [CrossRef]
  23. Corder, G.D.; Mclellan, B.C.; Green, S. Incorporating sustainable development principles into minerals processing design and operation: SUSOP®. Miner. Eng. 2010, 23, 175–181. [Google Scholar] [CrossRef]
  24. OECD. Review of DAC principles for development assistance. In Evaluation DWPoA, Editor; OECD: Paris, France, 1998. [Google Scholar]
  25. United Nations. Transforming Our World: The 2030 Agenda for Sustainable Development. 2015. Available online: https://sustainabledevelopment.un.org/content/documents/21252030%20Agenda%20for%20Sustainable%20Development%20web.pdf (accessed on 13 September 2022).
  26. United Nations. The 2030 Agenda and the Sustainable Development Goals: An Opportunity for Latin America and the Caribbean. 2018. Available online: https://repositorio.cepal.org/bitstream/handle/11362/40156/25/S1801140_en.pdf (accessed on 15 September 2022).
  27. Mansell, P.; Philbin, S. Measuring Sustainable Development Goals Target on Infrastructure Projects. JMPM 2020, 8, 42–63. [Google Scholar] [CrossRef]
  28. Keeys, L.A.; Huemann, M. Project benefits co-creation: Shaping sustainable development benefits. Int. J. Proj. Manag. 2017, 35, 1196–1212. [Google Scholar] [CrossRef]
  29. Morris, P. Climate Change and What the Project Management Profession Should be Doing About It. Association for Project Management. 2017. Available online: https://www.apm.org.uk/media/7496/climate-change-report.pdf (accessed on 15 September 2022).
  30. IPCC. Climate Change 2022: Impacts, Adaptation and Vulnerability. Contribution of Working Group II to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change; Pörtner, H.-O., Roberts, D.C., Tignor, M., Poloczanska, E.S., Mintenbeck, K., Alegría, A., Craig, M., Langsdorf, S., Löschke, S., Möller, V., Okem, A., Rama, B., Eds.; Cambridge University Press: Cambridge, UK, 2022; p. 3056. [Google Scholar] [CrossRef]
  31. Silvius, A.J.; Schipper, R.P. Sustainability in project management: A literature review and impact analysis. Soc. Bus. 2014, 4, 63–96. [Google Scholar] [CrossRef]
  32. Government of Canada. List of Projects Funded by the Sustainable Development Goals Funding Program. Available online: https://www.canada.ca/en/employment-social-development/programs/sustainable-development-goals/projects-funded.html (accessed on 17 October 2022).
  33. The University of Newcastle. Sustainable Development Goals. Available online: https://www.newcastle.edu.au/our-uni/sustainable-development-goals/specific-projects (accessed on 17 October 2022).
  34. Asia Society. Project Planning Template. Available online: https://asiasociety.org/sites/default/files/inline-files/01_UN_SDG_No%20Poverty_FINAL.pdf (accessed on 17 October 2022).
  35. Google Developers Student Clubs. The 17 Sustainable Development Goals of the United Nations. Available online: https://developers.google.com/community/gdsc-solution-challenge/UN-goals (accessed on 17 October 2022).
  36. Sachs, J.; Lafortune, G.; Kroll, C.; Fuller, G.; Woelm, F. Sustainable Development Report 2022. Cambridge University Press: Cambridge, UK, 2022; p. 508. [Google Scholar] [CrossRef]
  37. World Bank. Theme Taxonomy and definitions. 2016. Available online: https://thedocs.worldbank.org/en/doc/275841490966525495-0290022017/original/NewThemeTaxonomyanddefinitionsrevisedJuly012016.pdf (accessed on 15 September 2022).
  38. Chui, M.; Harrison, M.; Manyika, J.; Roberts, R.; Chung, R.; van Heteren, A.; Nel, P. Notes from the AI frontier: Applying AI for Social Good; McKinsey Global Institute: New York, NY, USA, 2018; Available online: https://ec.europa.eu/futurium/en/system/files/ged/mgi-applying-ai-for-social-good-discussion-paper-dec-2018.pdf (accessed on 15 September 2022).
  39. Pedemonte, V. AI for sustainability: An Overview of AI and the SDGs to Contribute to the European Policy-Making. 2020. Available online: https://ec.europa.eu/futurium/en/system/files/ged/vincent-pedemonte_ai-for-sustainability_0.pdf (accessed on 15 September 2022).
  40. United Nations. Agenda 21. In Proceedings of the United Nations Conference on Environment & Development, Rio de Janeiro, Brazil, 3–14 June 1992. [Google Scholar]
  41. International Telecommunication Union. AI for Good Global Summit ITU News Magazine 02/2020. 2020. Available online: https://www.itu.int/hub/pubs/itu-news-magazine/ (accessed on 15 September 2022).
  42. International Telecommunication Union. United Nations Activities on Artificial Intelligence (AI) [Online]. 2019. Available online: https://www.itu.int/dms_pub/itu-s/opb/gen/S-GEN-UNACT-2019-1-PDF-E.pdf (accessed on 15 September 2022).
  43. Zhao, C.; Luan, J. Data mining: Going beyond traditional statistics. New Dir. Inst. Res. 2006, 131, 7–16. [Google Scholar] [CrossRef]
  44. Sancho, F. Introducción al Aprendizaje Automático. Universidad de Sevilla, España. 2015. Available online: http://www.cs.us.es/~fsancho/?e=75 (accessed on 15 September 2022).
  45. Faggella, D. "¿Qué es la Inteligencia Artificial? Una Definición Informada". Emerj Artificial Intelligence Research. 2018. Available online: https://emerj.com/ai-glossary-terms/what-is-artificial-intelligence-an-informed-definition (accessed on 15 September 2022).
  46. Morfaw, J. Fundamentals of project sustainability. In Proceedings of the PMI® Global Congress 2014, Phoenix, AZ, USA, 25–28 October 2014. [Google Scholar]
  47. Thiele, L.P. Sustainability, 2nd ed.; Polity Press: Cambridge, UK, 2016. [Google Scholar]
  48. Azcona, M.; Manzini, F.; Dorati, J. Precisiones metodológicas sobre la unidad de análisis y la unidad de observación: Aplicación a la investigación en psicología. In Proceedings of the IV Congreso Internacional de Investigación, La Plata, Argentina, 13–15 November 2013; Available online: http://www.memoria.fahce.unlp.edu.ar/trab_eventos/ev.12219/ev.12219.pdf (accessed on 18 August 2022).
  49. Martinsuo, M.; Huemann, M. Designing case study research. Int. J. Proj. Manag. 2021, 39, 417–421. [Google Scholar] [CrossRef]
  50. Hernández, R.; Fernández, C.; Baptista, P. Metodología de la Investigación, 3rd ed.; McGraw-Hill: New York, USA, 2003; Available online: http://catarina.udlap.mx/u_dl_a/tales/documentos/lad/pinera_e_rd/capitulo3.pdf (accessed on 15 September 2022).
  51. Pérez, F.J.; Martínez, P.; Martínez, M. Satisfacción del estudiante universitario con la tutoría. Diseño y validación de un instrumento de medida. Estud. Sobre Educ. 2015, 29, 81–101. [Google Scholar] [CrossRef] [Green Version]
  52. Torres, M.; Karim, P. Tamaño de una Muestra Para una Investigación de Mercado. Boletín Electrónico. Facultad de Ingeniería, Universidad Rafael Landívar, Ciudad de Guatemala, Guatemala. 2021. Available online: https://docplayer.es/424351-Tamano-de-una-muestra-para-unainvestigacion-de-mercado.html (accessed on 19 August 2022).
  53. Unión Mundial para la Naturaleza. Informe Anual. 1998. Available online: https://portals.iucn.org/library/sites/library/files/documents/1999-031-Es.pdf (accessed on 15 September 2022).
  54. Tastle, W.; Wierman, M.J. Consensus and dissention: A Measure of Ordinal Dispersion. Int. J. Approx. Reason. 2007, 45, 531–545. [Google Scholar] [CrossRef] [Green Version]
  55. Encarnación, Y. La lógica difusa aplicada al sector manufacturero. Cienc. Y Soc. 2013, 38, 793–814. [Google Scholar] [CrossRef]
  56. Wierman, M.J.; Tastle, W. Consensus and dissention: Theory and properties. In Proceedings of the Fuzzy Information Processing Society NAFIPS 2005, Annual Meeting of the North American, Detroit, MI, USA, 26–28 June 2005. [Google Scholar] [CrossRef]
  57. Mamdani, E.H.; Assilian, S. An experiment in linguistic synthesis with a fuzzy logic controller. Int. J. ManMachine Stud. 1975, 7, 1–13. [Google Scholar] [CrossRef]
  58. Huitzil, I.; Lacramioara, J.B.; Bobillo, F. Gait recognition using fuzzy ontologies and kinect sensor data. Int. J. Approx. Reason. 2019, 113, 354–371. [Google Scholar] [CrossRef]
  59. Dass, S.; Gary, K.; Cunningham, J. Predicting student dropout in self-paced MOOC course using Random Forest model. Information 2021, 12, 476. [Google Scholar] [CrossRef]
  60. Chen, Z.; Yu, W.; Zhou, L. ADASYN—Random Forest based intrusion detection model. In Proceedings of the 4th International Conference on Signal Processing and Machine Learning, Beijing, China, 18–20 August 2021. [Google Scholar] [CrossRef]
  61. Rodríguez, J.; Reguant, M. Calcular la fiabilidad de un cuestionario o escala mediante el SPSS: El coeficiente alfa de Cronbach. REIRE Rev. D’innovació I Recer. En Educ. 2020, 13, 1–13. [Google Scholar] [CrossRef]
  62. Le Blanc, D. Towards integration at last? The sustainable development goals as a network of targets. Sustain Dev. 2015, 23, 176–187. [Google Scholar] [CrossRef]
  63. Weng, C.G.; Poon, J. A new evaluation measure for imbalanced datasets. In Proceedings of the 7th Australasian Data Mining Conference, Adelaide, Australia, 27–28 November 2008. [Google Scholar]
  64. Chen, C.; Breiman, L. Using Random Forest to Learn Imbalanced Data; University of California: Berkeley, CA, USA, 2004. [Google Scholar]
  65. Mansell, P.; Philbin, S.P.; Broyd, T.; Nicholson, I. Assessing the impact of infrastructure projects on global sustainable development goals. Proc. Inst. Civ. Eng. Eng. Sustain. 2019, 173, 196–212. [Google Scholar] [CrossRef]
  66. Porter, M.E.; Kramer, M.R. The Big Idea: Creating Shared Value, Rethinking Capitalism. Harv. Bus. Rev. 2011, 89, 62–77. [Google Scholar]
  67. Klopp, J.M.; Petretta, D.L. The urban sustainable development goal: Indicators, complexity and the politics of measuring cities. Cities 2017, 63, 92–97. [Google Scholar] [CrossRef]
  68. Donohue, I.; Hillebrand, H.; Montoya, J.M.; Petchey, O.L.; Pimm, S.L.; Fowler, M.S.; O’Connor, N.E. Navigating the complexity of ecological stability. Ecol. Lett. 2016, 19, 1172–1185. [Google Scholar] [CrossRef] [Green Version]
  69. Harrison, F.; Lock, D. Advanced Project Management: A Structured Approach, 4th ed.; Gower Publishing Limited: Aldershot, UK, 2004; Volume 80. [Google Scholar]
  70. Griffin, A.; Page, A.L. PDMA success measurement project: Recommended measures for product development success and failure. J. Prod. Innov. Manag. 1996, 13, 478–496. [Google Scholar] [CrossRef]
  71. Fernández, G.; Rodríguez, F. A methodology to identify sustainability indicators in construction project management—Application to infrastructure projects in Spain. Ecol. Indic. 2010, 10, 1193–1201. [Google Scholar] [CrossRef]
  72. Müller, R.; Turner, R. The influence of project managers on project success criteria and project success by type of project. Eur. Manag. J. 2007, 25, 298–309. [Google Scholar] [CrossRef]
  73. Sachs, J.; Kroll, C.; Lafortune, G.; Fuller, G.; Woelm, F. Sustainable Development Report 2021. In The Decade of Action for the Sustainable Development Goals; Cambridge University Press: Cambridge, UK, 2021. [Google Scholar] [CrossRef]
  74. United Nations. Quadrennial report on regional progress and challenges in relation to the 2030 Agenda for Sustainable Development in Latin America and the Caribbean. In Proceedings of the Foro de los países de América Latina y el Caribe sobre Desarrollo Sostenible, Santiago de Chile, Chile, 24–26 April 2019. [Google Scholar]
  75. Vinuesa, R.; Azizpour, H.; Leite, I.; Balaam, M.; Dignum, V.; Domisch, S.; Felländer, A.; Langhans, S.D.; Tegmark, M.; Nerini, F. The role of artificial intelligence in achieving the Sustainable Development Goals. Nat. Commun 2020, 11, 233. [Google Scholar] [CrossRef] [Green Version]
  76. García, A.; Gracia, S.; Cisteró, J.; Estay, C.; Fernández-Ros, J.; Álvarez, A. Metodología de Enseñanza-Aprendizaje Colaborativo y Cooperativo Basada en la Resolución de Problemas-Proyectos Con Soporte de Entornos Virtuales de Trabajo; VI Jornadas sobre Aprendizaje Cooperativo, Universitat Politécnica de Catalunya (UPC): Barcelona, Spain, 2006. [Google Scholar]
  77. Blasco, J.; Cisteró, J.; Estay, C.; Ferrari, E.; García, A.; Gracia, S.; Sánchez, V. Enfoque metodológico para la mejora de la docencia mediante la aplicación de entorno colaborativo en la asignatura de proyectos de ingeniería. In Proceedings of the En Actas CIDUI 2002 del Congreso Internacional Docencia Universitaria e Innovación, Tarragona, España, 1–3 July 2002. [Google Scholar]
  78. Jun, P. Classification of Imbalanced Data Using Synthetic Over-Sampling Techniques. University of California, USA. 2015. Available online: https://escholarship.org/content/qt72w743h7/qt72w743h7_noSplash_bd589490abd5ac433d09090e910cb967.pdf (accessed on 15 September 2022).
  79. Demidova, L.; Klyueva, I. Improving the Classification Quality of the SVM Classifier for the Imbalanced Datasets on the Base of Ideas the SMOTE Algorithm. Int. Jt. Conf. Mater. Sci. Mech. Eng. CMSME 2017, 10, 1–4. [Google Scholar] [CrossRef]
Figure 1. Global SDG Index Score (0–100) for some countries of Latin America and the Caribbean (2015–2022). Note. The difference at 100 is the distance needed in percentage to achieve the SDGs. Data are derived from indicators provided by official United Nations statistics and other non-traditional statistics, such as university centers and non-governmental organizations [36].
Figure 1. Global SDG Index Score (0–100) for some countries of Latin America and the Caribbean (2015–2022). Note. The difference at 100 is the distance needed in percentage to achieve the SDGs. Data are derived from indicators provided by official United Nations statistics and other non-traditional statistics, such as university centers and non-governmental organizations [36].
Applsci 12 11188 g001
Figure 2. Number of project initiatives that fully or partially link AI to the SDGs. Note. Adapted from [38].
Figure 2. Number of project initiatives that fully or partially link AI to the SDGs. Note. Adapted from [38].
Applsci 12 11188 g002
Figure 3. SDG indicator assessment method.
Figure 3. SDG indicator assessment method.
Applsci 12 11188 g003
Figure 4. Main indicators of the SDGs used by experts. Note. Own elaboration.
Figure 4. Main indicators of the SDGs used by experts. Note. Own elaboration.
Applsci 12 11188 g004
Figure 5. Frequency distribution of the “Level of Sustainability” variable and overprinted normal distribution curve. Note. The lower (64) and upper (76) cut-off values for the determination of class categories are represented.
Figure 5. Frequency distribution of the “Level of Sustainability” variable and overprinted normal distribution curve. Note. The lower (64) and upper (76) cut-off values for the determination of class categories are represented.
Applsci 12 11188 g005
Figure 6. Overall sustainability index of the sample of projects based on the input consensus. Note. Own elaboration.
Figure 6. Overall sustainability index of the sample of projects based on the input consensus. Note. Own elaboration.
Applsci 12 11188 g006
Figure 7. Comparison of the overall accuracy metric for different classifiers during the training phase of the unbalanced model. Note: The orange horizontal line refers to the median and the green triangle to the mean of the indicator.
Figure 7. Comparison of the overall accuracy metric for different classifiers during the training phase of the unbalanced model. Note: The orange horizontal line refers to the median and the green triangle to the mean of the indicator.
Applsci 12 11188 g007
Figure 8. Comparison of the overall accuracy metric for different classifiers during the training phase of the balanced model. Note: The orange horizontal line refers to the median and the green triangle refers to the mean.
Figure 8. Comparison of the overall accuracy metric for different classifiers during the training phase of the balanced model. Note: The orange horizontal line refers to the median and the green triangle refers to the mean.
Applsci 12 11188 g008
Table 1. Basic descriptors to achieve a project manager’s TBL competences during the evaluation stage.
Table 1. Basic descriptors to achieve a project manager’s TBL competences during the evaluation stage.
MaterialsTBL Descriptors
Project marketGeneral aspects of the industry. Background study. Demand from potential clients. Entry barriers.
Project profitabilitySocial profitability vs. economic profitability. Compensation of monetary deficit. Subsidies, grants, and aids.
Social investment projectsPromotion of local development. Support for the traditions and rights of indigenous communities. Private vs. social evaluation.
Technology and environment in the projectPollution prevention and control. Environmental risk management. Biodiversity preservation. Fight against climate change. Life cycle analysis. Environmental Impact Assessment. Compliance with legal or social regulatory requirements.
Project risk and
uncertainty
Socioeconomic risk mitigation measures. Sensitivity analysis of sustainability projects.
Note. Own elaboration.
Table 2. The most valued indicators of the different sustainability models of project management in the areas of engineering and administration, according to Martens and Carvalho.
Table 2. The most valued indicators of the different sustainability models of project management in the areas of engineering and administration, according to Martens and Carvalho.
DimensionNumber of Variables
Identified
Indicators
Economic158Survival of the organization
Cost management
Stakeholder relations
Employee welfare
Environmental248Air, water, energy, and soil
Waste generation
Material consumption
Other *
Social270Good labor practices
Community relations
Child labor
Human rights
Impact of products and services
Financing of social actions
Note. Adapted from Martens and Carvalho [8]. * It refers to compliance with legislation, global warming, noise, environmental policies, training, and environmental education.
Table 3. List of Sustainable Development Goals (SDGs).
Table 3. List of Sustainable Development Goals (SDGs).
NumberSDGsNumberSDGs
1No poverty10Reduced inequalities
2Zero hunger11Sustainable cities and communities
3Good health and well-being12Responsible consumption and production
4Quality education13Climate action
5Gender equality14Life below water
6Clean water and sanitation15Life on land
7Affordable and clean energy16Peace, justice, and strong institutions
8Decent work and economic growth17Partnerships for said goals
9Industry, innovation, and infrastructure
Note. United Nations [20].
Table 4. Sub-sample list of 10 sustainability projects for local communities in Latin America and the Caribbean.
Table 4. Sub-sample list of 10 sustainability projects for local communities in Latin America and the Caribbean.
IDProjectDimensions *SDGs **
1Design and construction of infrastructure and public spaces on the right bank of the Chorobamba River in the city of Oxapampa, PerúInfrastructure management
Public and social sector management
Partnerships for the goals
Clean water and sanitation
Sustainable cities and communities
Industry, innovation, and infrastructure
Life on land
2Wastewater treatment plant based on an oxidation lagoon for Los Portales housing, Piura, PerúInfrastructure management
Environment
Industry, innovation, and infrastructure
Clean water and sanitation
Life on land
3Technical trade training center for low-income youth, ChileEquality and inclusion
Economic empowerment
Education
Quality education
Reduced inequalities
Gender equality
Decent work and economic growth
No poverty
4MSW sorting plant from the Municipality of Yerba Buena, Tucumán, ArgentinaEconomic empowerment
Environment
Infrastructure management
Sustainable cities and communities
Responsible consumption and production
5Housing project in El Cantón Pedernales–Manabí, EcuadorEquality and inclusion
Economic empowerment
Reduced inequalities
Gender equality
No poverty
6Urban renewal plan for sidewalks surrounding the San Juan de Dios Hospital, San José, Costa RicaInfrastructure management
Public and social sector management
Partnerships for the goals
Sustainable cities and communities
Industry, innovation, and infrastructure
Life on land
7Environmental management plan for solid waste and organic waste generated by tourism activities around the Combeima River, Ibagué, ColombiaEnvironment
Public and social sector management
Economic empowerment
Partnerships for the goals
Clean water and sanitation
Sustainable cities and communities
Life below water
8Playa del Carmen Urban Planning Program, Quintana Roo, MexicoInfrastructure management
Public and social sector management
Partnerships for the goals
Sustainable cities and communities
Industry, innovation, and infrastructure
Life on land
9Accessibility program for people with disabilities in recreational spaces, San Pedro Sula, HondurasEquality and inclusion
Economic empowerment
Reduced inequalities
Gender equality
Decent work and economic growth
10Training program for coffee producers in the municipality of Mesetas, Meta, ColombiaEquality and inclusion
Economic empowerment
Education
Quality education
Reduced inequalities
Gender equality
Decent work and economic growth
No poverty
Note. * Adapted from [37] and [38]. ** The most significant SDGs are shown.
Table 5. UN activities on artificial intelligence (AI) and relationship with the SDGs.
Table 5. UN activities on artificial intelligence (AI) and relationship with the SDGs.
PartnersAI ActivitiesRelated SDGs
Food and Agriculture Organization of the United Nations (FAO)Fishing gear identification
Animal disease identification from images
Aquaculture mapping
Detecting fall armyworm infestations
1–3
8,9
10–12
International Labor Organization (ILO)From industrial robots to deep learning robots: the impact on jobs and employment
The economics of artificial intelligence: Implications for the future of work
Skills strategies for future labor markets
1–5
8–10
16,17
International Maritime Organization (IMO)Maritime Autonomous Surface Ships (MASS)
E-navigation
Marine Environmental Protection and AI
AI for Sustainable Maritime Transport (AI-SMART)
8,9,
11,13,14,
16,17
International Organization for Migration (IOM)Humanitarian Data Science and Ethics Group
IOM—Global Migration Data Analysis Centre (GMDAC)
Applying techniques for internal quality control within the Displacement Tracking Matrix (DTM) Global Team
7,10
17
United Nations Program on HIV/AIDSHealth Innovation Exchange & TimBre
Project: AIR-TB
3,4
9
17
United Nations Environment Program (UNEP)Water-Related Ecosystems—SDG 6.6.1
UNEP Q & A Chatbot
Funding Analysis and Prediction platform
UNEP Robotic Process Automation
6
17
World Bank GroupCreating Global Public Goods
Developing Knowledge and Policies
Piloting Disruptive Technologies in World Bank operations
Education-Use AI for Learning through Games
Due Diligence—Predicting accounting red flags from external financial reports
1–3
9–11
13,16
Note. Adapted from [41].
Table 6. Research design.
Table 6. Research design.
Unit of
Analysis:
Sustainability of multi-sectorial projects in Latin America and the Caribbean
Dependent variable:Level of implementation of Sustainable Development Goals
Operational definition of the variable
Applsci 12 11188 i001
Values of the dependent variable:High, medium, low
Independent variables:Sustainable Development Goals
How do you collect data on the presence or absence of the Sustainable Development Goals in your projects?
Applsci 12 11188 i002
Unit of observation:Responses to Likert-scale questionnaires administered to expert panels
Note. Adapted from [48,49].
Table 7. Basic statistical parameters of project distributions among the groups of experts.
Table 7. Basic statistical parameters of project distributions among the groups of experts.
Expert GroupNumber of ProjectsMeanStandard Deviation
1404.09000.53340
2414.12440.54067
3404.00230.51783
4334.07520.43769
5323.98500.47944
Note. Own elaboration.
Table 8. Expert consensus interpretation.
Table 8. Expert consensus interpretation.
IntervalConsensus Classification
C n s X 90 % Very strong consensus
80 % C n s X < 90 % Strong consensus
60 % C n s X < 80 % Moderate consensus
40 % C n s X < 60 % Balance
20 % C n s X < 40 % Moderate dissent
10 % C n s X < 20 % Strong dissent
C n s X < 10 % Very strong dissent
Note. Adapted from [56].
Table 9. Classification algorithms and their characteristics.
Table 9. Classification algorithms and their characteristics.
Classification AlgorithmsFeatures
Dummy Classifier (DMC)It establishes an average reference metric (accuracy) and its standard deviation, by means of which to compare the rest of the classification algorithms.
Fuzzy ClassifierA different number of templates can belong partially to one class or to several classes. Class membership is measured by a number μ A x   in the interval [0,1], where
μ A x = 0 ,     x A 1 ,     x   A 0 , 1           x   A p  
where “A” is the class and “x” is the vector of characteristics or pattern.
Logistic Regression (LR)It predicts the probability of an event or class occurring, conditional on a set of “n” independent variables. The model always returns the most probable class.
K-Nearest Neighbors (KNN)During the training phase, it searches for the K-nearest neighbors of the point to be classified and subjects them to majority voting—for example, by weighting each neighbor’s vote, according to the inverse square of their distances. An odd number of K will always be used to avoid possible ties.
Support Vector Machine (SVM)It has also been reformulated for regression. The objective is to obtain the best “n-1” dimensional hyperplane to optimally separate one class from another, where “n” is the number of coordinate axes or independent variables. It is more efficient than KNN in terms of cost and accuracy.
AdaBoost (Adaptive Boosting)It identifies those cases misclassified during training with several weak or base classifiers, giving them a higher weight or importance in successive cycles until the process stops for a certain minimum error value. Lastly, a final robust classifier is constructed as a weighted sum of the previous classifiers.
Gaussian Process ClassifierThey are used for both regression and classification. They are based on the Gaussian probability distribution. As with SVMs, they require the specification of a covariance function (or kernel). The Gaussian process makes predictions with uncertainty and works well with a small data set, as is the case in this study.
Random ForestIt results from a combination of multiple decision trees created during the training phase. Each decision tree votes for one class, with the final result being the class with the highest number of votes in the entire forest.
Note. Own elaboration.
Table 10. Performance evaluation metrics for a classification model.
Table 10. Performance evaluation metrics for a classification model.
MetricDescription
Overall   accuracy   rate = tp + tn tp + fp + fn + tn Overall hit percentage. Not a good indicator for unbalanced data.
Individual   accuracy   for   class   A = tn tn + fn Individual percentage hit rate per class. Can be used for unbalanced data.
Individual   accuracy   for   class   B = fp fp + tp
Sensitivity   recall = tp tp + fn Proportion of positive cases correctly identified by the classifier. Determines when false negative costs are high.
Specificity = tn tn + fp Proportion of negative cases correctly identified by the classifier.
Precision = tp tp + fp Model quality level. Determines when false positive costs are high.
f 1 score = 2 · precision · recall precision + recall Is used to easily compare measures of precision and sensitivity in a single value. It is very useful for binary classification problems where the study is focused on the positive class, as is the case here.
Receiver Operating Characteristics (ROC) and Area Under Curve (AUC)ROC is a probability curve that represents the fp rate on the abscissa axis and the tp rate on the ordinate axis for different thresholds. It indicates how much the model is able to distinguish between classes. The area under the AUC curve classifies the performance. The closer AUC is to unity, the better the model distinguishes between classes.
Note. tp: true positive; tn: true negative; fp: false positive; fn: false negative.
Table 11. Statistics associated with Cronbach’s Alpha.
Table 11. Statistics associated with Cronbach’s Alpha.
ItemScaling Average if the Element Has Been SuppressedScale Variance if the Element Has Been SuppressedTotal Correlation of Corrected
Elements
Cronbach’s Alpha if the Item Has Been Deleted
165.4757.9370.2970.865
265.0659.3420.2230.867
365.3057.4870.3440.863
465.5354.9960.5930.854
565.5856.2770.3880.862
665.2257.8020.3560.863
765.7054.2660.6000.853
865.5354.5210.5800.854
965.9454.4610.5600.855
1065.9653.2470.6040.852
1165.9053.2920.6090.852
1265.9652.8630.6120.852
1365.6455.1720.5250.856
1465.8554.3120.4260.862
1565.3457.1780.3850.862
1665.9453.4940.5400.855
1766.0453.4850.5730.854
Table 12. Consensus measurement criteria.
Table 12. Consensus measurement criteria.
DimensionSDGsConsensus
Mean
Environmental6, 7, 11–1571.56
Social1–5, 7, 8, 10–12, 16, 1771.78
Economic7–9, 11, 1271.52
Mean71.66
SD3.70
Table 13. Percentage of sustainability level by grouping ranges.
Table 13. Percentage of sustainability level by grouping ranges.
ClassGrouping RangeFrequency%
LowValues ≤ 644021.5
MediumValues 64–7611260.2
HighValues ≥ 763418.3
Note. Own elaboration.
Table 14. Set of metrics of the unbalanced models (testing phase).
Table 14. Set of metrics of the unbalanced models (testing phase).
ClassifierClasstptnfpfnAccuracyOverall
Accuracy
PrecisionRecallF1 ScoreROC/AUC
LRHigh529220.890.840.710.710.710.98
Low630020.951.000.750.861.00
Medium2111420.840.840.910.870.97
SVMHigh630110.950.890.860.860.860.98
Low630020.951.000.750.861.00
Medium2212310.890.880.960.920.97
RFHigh530120.920.790.830.710.770.98
Low330050.871.000.380.551.00
Medium228710.790.760.960.850.94
KNNHigh629210.920.840.750.860.800.99
Low530030.921.000.620.770.88
Medium2111420.840.840.910.870.90
Table 15. Set of metrics of the balanced models (testing phase).
Table 15. Set of metrics of the balanced models (testing phase).
ClassifierClasstptnfpfnAccuracyOverall
Accuracy
PrecisionRecallF1 ScoreROC/AUC
LRHigh729200.950.890.781.000.880.98
Low630020.951.000.750.861.00
Medium2113220.890.910.910.910.97
SVMHigh729200.950.920.781.000.880.99
Low730010.971.000.880.931.00
Medium2114120.920.950.910.930.98
GAUSSHigh530120.920.870.830.710.770.98
Low630020.951.000.750.861.00
Medium2211410.870.850.960.900.97
KNNHigh729200.950.870.781.000.880.98
Low629120.920.860.750.800.99
Medium2013230.870.910.870.890.95
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

García Villena, E.; Pascual Barrera, A.; Álvarez, R.M.; Dzul López, L.A.; Tutusaus Pifarré, K.; Vidal Mazón, J.L.; Miró Vera, Y.A.; Brie, S.; López Flores, M.A. Evaluation of the Sustainable Development Goals in the Diagnosis and Prediction of the Sustainability of Projects Aimed at Local Communities in Latin America and the Caribbean. Appl. Sci. 2022, 12, 11188. https://doi.org/10.3390/app122111188

AMA Style

García Villena E, Pascual Barrera A, Álvarez RM, Dzul López LA, Tutusaus Pifarré K, Vidal Mazón JL, Miró Vera YA, Brie S, López Flores MA. Evaluation of the Sustainable Development Goals in the Diagnosis and Prediction of the Sustainability of Projects Aimed at Local Communities in Latin America and the Caribbean. Applied Sciences. 2022; 12(21):11188. https://doi.org/10.3390/app122111188

Chicago/Turabian Style

García Villena, Eduardo, Alina Pascual Barrera, Roberto Marcelo Álvarez, Luís Alonso Dzul López, Kilian Tutusaus Pifarré, Juan Luís Vidal Mazón, Yini Airet Miró Vera, Santiago Brie, and Miguel A. López Flores. 2022. "Evaluation of the Sustainable Development Goals in the Diagnosis and Prediction of the Sustainability of Projects Aimed at Local Communities in Latin America and the Caribbean" Applied Sciences 12, no. 21: 11188. https://doi.org/10.3390/app122111188

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