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A feasible proposal for energy-efficient roof retrofitting in southern European obsolete residential neighborhoods

Domínguez Torres, Carlos Antonio; Domínguez Torres, Helena; Hernández Valencia, Miguel; Roa Fernández, Jorge; Herrera-Limones, Rafael

Abstract

1960s Europe saw a large number of residential neighborhoods built to house those migrating from the countryside. Today, more than 50 years later, these neighborhoods suffer high levels of functional, social, and technical obsolescence. In response to this, the University of Seville developed the Aura Strategy as an intervention methodology to find global solutions to issues in outdated neighborhoods. To provide visibility to this aspect of the Aura Strategy, the retrofit proposal presented in this article provides a solution to improve the roofing of buildings in a case study neighborhood (Polígono de San Pablo, Seville) and an analysis of the results in terms of energy and financial savings for local residents. The results show that for a population of roughly 18,000 (in 2018), net savings, including energy and retrofitting costs, ranging from nearly e6.5 to over e8.6 million can be made over the 20-year life-cycle span. Likewise, the results obtained on the reduction of thermal loads indicate a 72% decrease in energy consumption, equivalent to a saving of close to 4500 tons of greenhouse gas emissions for the district and the entire life-cycle time period, with the consequent benefits on the impact on air quality and the fight against climate change.

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Citation: Domínguez-Torres, C.-A.; Domínguez-Torres, H.; Hernández-Valencia, M.; Roa-Fernández, J.; Herrera-Limones, R. A Feasible Proposal for Energy-Efficient Roof Retrofitting in Southern European Obsolete Residential Neighborhoods. Buildings 2024,14, 88. https://doi.org/ 10.3390/buildings14010088 Academic Editor: Alessandro Prada Received: 20 October 2023 Revised: 18 December 2023 Accepted: 25 December 2023 Published: 28 December 2023 Copyright: © 2023 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https:// creativecommons.org/licenses/by/ 4.0/). buildings Article A Feasible Proposal for Energy-Efficient Roof Retrofitting in Southern European Obsolete Residential Neighborhoods Carlos-Antonio Domínguez-Torres 1,2, Helena Domínguez-Torres 3,4 , Miguel Hernández-Valencia 5,6 , Jorge Roa-Fernández 5,7 and Rafael Herrera-Limones 5,6,* 1Escuela Técnica Superior de Arquitectura, Universidad de Sevilla, Avda.Reina Mercedes 2, 41012 Sevilla, Spain; [email protected] 2Research Group TEP130, Universidad de Sevilla, 41012 Sevilla, Spain 3Facultad de Ciencias Económicas y Empresariales, Universidad de Sevilla, Avda.Ramón y Cajal, 1, 41018 Sevilla, Spain; [email protected] 4Research Group SEJ490, Universidad de Sevilla, 41012 Sevilla, Spain 5Instituto Universitario de Arquitectura y Ciencias de la Construcción, Escuela Técnica Superior de Arquitectura, Universidad de Sevilla, Av. Reina Mercedes 2, 41012 Sevilla, Spain; [email protected] (M.H.-V.); [email protected] (J.R.-F.) 6Research Group HUM 965, Universidad de Sevilla, 41012 Sevilla, Spain 7Research Group TEP 206, Universidad de Sevilla, 41012 Sevilla, Spain *Correspondence: herr[email protected] Abstract: 1960s Europe saw a large number of residential neighborhoods built to house those migrating from the countryside. Today, more than 50 years later, these neighborhoods suffer high levels of functional, social, and technical obsolescence. In response to this, the University of Seville developed the Aura Strategy as an intervention methodology to find global solutions to issues in outdated neighborhoods. To provide visibility to this aspect of the Aura Strategy, the retrofit proposal presented in this article provides a solution to improve the roofing of buildings in a case study neighborhood (Polígono de San Pablo, Seville) and an analysis of the results in terms of energy and financial savings for local residents. The results show that for a population of roughly 18,000 (in 2018), net savings, including energy and retrofitting costs, ranging from nearly e 6.5 to over e 8.6 million can be made over the 20-year life-cycle span. Likewise, the results obtained on the reduction of thermal loads indicate a 72% decrease in energy consumption, equivalent to a saving of close to 4500 tons of greenhouse gas emissions for the district and the entire life-cycle time period, with the consequent benefits on the impact on air quality and the fight against climate change. Keywords: urban sustainability; social construction; retrofit energy saving measures; aging effect; thermal dynamic model; numerical methods; life cycle cost analysis 1. Introduction The neighborhoods built in Europe during the 1950s and 1960s in response to the mass migration of workers from the countryside to cities need rehabilitation. To do so, architectural retrofitting should be considered rather than demolition or new construction. To reduce the carbon footprint of the process, the intervention strategy in these outdated neighborhoods should be based on methodologies that enable the refurbishment and transformation of buildings through the conservation and reuse of the existing urban fabric instead of demolition and the generation of new buildings. This is the intervention methodology proposed by the Aura Strategy. This strategy has been developed by a group of researchers from the University of Seville and has been tested in various editions of the Solar Decathlon competition [ 1 , 2 ]. It is currently being applied in the Polígono San Pablo neighborhood within the framework of the “Direct application of the SOLAR DECATHLON-U.S Team Aura Strategy in the rehabilitation of obsolete Andalusian neighborhoods” research project financed by the regional government of Andalusia, Spain. The Buildings 2024,14, 88. https://doi.org/10.3390/buildings14010088 https://www.mdpi.com/journal/buildings Buildings 2024,14, 88 2 of 23 Aura Strategy is an “urban acupuncture strategy” that proposes a gradual requalification of social identity, material, and energy, ensuring an effective improvement in the health and comfort of residents, leading to an increase in quality of life. The Aura Strategy proposes actions centered on four lines of intervention. These are: • Comfort and Health • Materiality • Cultural Identity and Accessibility • Retrofitting and Energy The neighborhood of Polígono de San Pablo was selected for this study because it is an obsolete residential neighborhood, included in the Catalogue of Vulnerable Neighborhoods (VN) in Spain 2011 [ 3 ]. A Vulnerable Neighborhood is defined as an urban area of a certain homogeneity and urban continuity, delimited on the basis of an area of between 3500 and 15,000 inhabitants in which at least one of the three Basic Indicators of Urban Vulnerability (BIUV; BIUV Studies, BIUV Housing, or BIUV Unemployment) exceeds a value established as a vulnerability reference. The Aura Strategy is also applicable to other locations. For its application to other locations, the strategy is always based on a previous analysis of energy, materiality, social and cultural aspects, or identity. In this way, the response and actions can be adapted to specific and different locations, climates, and environments. The strategy is not the material solution but the methodology that determines this solution. This article examines the line of materiality and centers on one of the most evident weaknesses present in the buildings of this case study neighborhood: roofs. The aim of this research is to use a dynamic time-dependent analysis of the energy and economic variables of the life-cycle time span and to propose and assess a retrofit solution for the roofing of the buildings in the neighborhood of Polígono de San Pablo. This refurbishment solution is implemented with the purpose of reducing the energy consumption required to provide thermal comfort conditions in homes on the top floor, with the consequent benefits in the reduction of energy poverty, which has such a strong impact on the social context under study, while at the same time, through the consequent reduction of greenhouse gases, it implies important benefits for air quality and the fight against climate change. 1.1. Passive Roofs Strategies On a typical hot sunny day in the summer, as they usually are under mediterranean climate conditions, building rooftop surfaces can be 27–50 ◦ C hotter than the surrounding air temperature [ 4 ], which means that the heat transmitted by convection to the surrounding air and by thermal radiation to taller buildings can be very significant and contributes to urban heating and the so-called Urban Heat Island effect. Therefore, reducing the temperature of the rooftop influences the improvement of the quality of the urban environment [ 5 ] at the same time that it reduces the cooling loads necessary to obtain internal thermal comfort conditions [ 6 ], which in turn reduces the rejection of heat from heating systems, further strengthening the urban heat island while producing a decrease in greenhouse gas emissions through the reduction of energy consumption. A large body of research has been conducted for generating strategies for roof heat mitigation with multiple approaches, among which passive strategies are especially interesting in the context of this work. The role of the inclination and orientation of the rooftop was analyzed in [ 7 ] for lightweight and heavyweight roofs equipped or devoid of an insulation material during the cooling period in Italy and Greece. Different insulation materials in arid zones were studied in [ 8 ], where four different structures to cool the roof in Jordania were analyzed and it was found that clay thermal insulation over the roof provided the best results for cooling of the building for better comfort conditioning in arid areas. Buildings 2024,14, 88 3 of 23 In [ 9 ], using thermal models created with Energy Plus, the authors concluded that the use of cool roofs resulted in a 17% drop in the annual cooling demand for the building investigated in the urban region of Acharnes municipality in Greece. In [ 10 ], exploring the possibilities of energy savings, the research examined the effectiveness of dynamic cool roofs (DCRs) incorporating seasonally variable reflective surfaces across different building prototypes in comparison to static cool roofs. wherein the authors found that applying variable reflective coatings to buildings with low insulation levels can result in source energy savings, ranging between 4.33 and 19.44 MJ/m 2 (or 1.6–4.9%) for residential units and 1.17 and 18.00 MJ/m2(equivalent to 0.3–3.9%) for office structures. In [ 11 ], through the application of building energy simulation, the investigation focused on isolating the consequences of enhancing rooftop radiative properties on surface temperatures and heat fluxes. The results suggest that elevating rooftop solar reflectance from 0.2 to 0.96, with a fixed emissivity of 0.9, leads to an average reduction in rooftop temperature of approximately 10 ◦C. In [ 12 ], the effect of the installation of an innovative cool clay tile on the rooftop of historic residential buildings in central Italy was analyzed, and they found maximum primary energy saving for cooling about 51%, while the heating energy penalty was slower than 2%. A ventilated roof is proposed and implemented in [ 13 ] as a passive cooling technique that allows environmental heat sinks such as night ventilation and evaporative cooling. Energy impact analysis showed that implementing the ventilated roof solution can reduce cooling needs by 65% without a resulting heating penalty. In [ 14 ], different urban surface parameters were evaluated from several perspectives to assess their comparative effectiveness as heat mitigation strategies and concluded that roofs with high albedos are found to be the best heat mitigation for reducing daytime temperatures (0.85 albedo, 1.29 ◦ C) while green roofs show the best nighttime efficacy (100%,1.15 ◦C). In [ 15 ], three different cooling roof techniques were addressed: cool reflective white paint, white ceramic tiles, and a cool-ventilated roof. These techniques were analyzed by monitoring both roof surface temperatures and indoor temperatures. It was concluded that a cool-ventilated roof is the most efficient solution, reducing the average indoor temperature by 4.95 ◦C. In [ 16 ], the aging characteristics of high solar reflective index (SRI) or cool paints were assessed qualitatively, and the energy savings for their application in residential buildings were estimated. Diurnal Selective Radiative Cooling based in roof panels RC roofs was studied in [ 17 ], where it was found that in terms of surface temperature, RC panels outperformed high performance cool roofs, but in terms of anthropogenic heat reduction and microclimate air temperature reduction, they both had a similar impact. In [ 18 ], a literature review is conducted and a general framework is proposed that allows current modeling to go beyond typical protocols by including data relating a specific urban microclimate at the neighborhood/city level to that of a building, thus linking the environmental microclimate to the objective appraisal of building energy efficiency. On the other hand, in the framework of the Mediterranean climate, one of the proven effective measures to save cooling energy is through the use of a suitable combination of thermal insulation and a rooftop coating highly reflective of solar radiation; this combination, when well designed, has proven to provide significant savings energy to achieve thermal indoor comfort and to be cost efficient [ 19 , 20 ]. This combination of thermal insulation and cool coating is the constructive solution used here to retrofit the roof of the case study buildings considered in this work. Regarding the agreement of the results obtained in the present research with the previous literature, it can be said that for the energy and cost analyses, the results are consistent with the findings presented in [ 6 , 20 ] for the case of a single roof, without entering into a neighborhood context that is not addressed in these works cited. Buildings 2024,14, 88 4 of 23 1.2. The Case Study Approach Construction of the Polígono de San Pablo began in the year 1961. Around 57,000 people were expected to live there, divided into five districts (A, B, C, D, and E), each with 2000 homes, as seen in Figure 1. This research aims to quantify the relevance of planning a comprehensive intervention that covers all five districts of the neighborhood. The neighborhood includes different types of 4, 8, and 12 storey residential buildings. Among these, there are 707 free-standing buildings and an estimated 112,000 m 2 of roof area, Figure 2. Considering that most building types are two homes per floor, 1414 homes will benefit directly from this intervention. In other words, all of the top-story homes in each retrofitted building. The typical building roof plan is shown in Figure 3. This is a conventional typology of walkable roof with a ceramic coating. Figure 1. Districts of the Polígono de San Pablo neighborhood. Figure 2. Aerial photo taken using UAV technology. Buildings 2024,14, 88 5 of 23 Figure 3. Roof plan. 2. Materials and Methods 2.1. Methodology for Energy Computation This section outlines the methodology followed to evaluate the thermal energy crossing the roof. First, the physical assumptions are presented, then, the associated mathematical equations are shown, and finally, the aging effect for the retrofitted roof and its practical implementation are described. 2.1.1. Physical Framework In this section, the physical framework involving the heat flux through the roof is described. Specifically, thermal flux through the roofs is determined by the following: • Thermal gains due to solar radiation impacting the roof’s outer surface. • Infrared radiative heat transfer between the roof’s outer surface and the open sky and taller buildings. • Convective heat transfer between the roof’s exterior surface and the surrounding air. • Conduction-based thermal transfer within the roof’s multiple layers. • Convective heat transfer between the roof’s interior surface and the indoor air. • Infrared radiative heat transfer between the roof’s inner surface and the room indoor surfaces. Section 2.2.2 provides details on how to compute the solar radiation absorbed by the roof’s outer surface. This result is based on the solar radiation values obtained from climatic data, such as the Energy Plus Weather (EPW) files, or from monitoring data that are entered into the model. When computing the solar radiation gain, it is important to consider the absorptivity of the outer surface. As it is subject to the so-called ageing effect, it is non-constant in time. The pattern of change in the solar absorptivity of the outer surface of the roof is described in Section 2.3. The radiative heat exchange between the outer surface of the roof and the sky is computed by calculating the downward horizontal infrared radiation intensity through the use of the sky emissivity as described in Section 2.2.3. The convective heat transfer between the outer surface of the roof and the surrounding air is calculated by a two-fold approach: on the one hand, using convective heat transfer correlations to calculate the energy balance on the outer surface of the roof, and, on the other Buildings 2024,14, 88 6 of 23 hand, by calculating the thermal boundary layer of the air on the roof. Both procedures are described in Section 2.2.4. To estimate the heat transfer by conduction through the different layers of the roof, the physical model is based on the models of thermal conduction through a multilayer wall considering the different thermophysical values of each layer that makes up the roof as described in Section 2.2.5. Finally, the infrared radiative and convective heat transfer between the roof’s inner surface and the building indoor is carried out using a combined convective-radiative transfer coefficient applied to the energy balance on the inner roof surface as described in Section 2.2.5. 2.2. Mathematical Formulation In this section, drawing on the physical principles established in the earlier section, we bring forth the mathematical equations relevant to heat transfer across the roof. 2.2.1. Energy Balance on the Outer Roof Surface As a result of the energy processes taking place on the outer surface of the roof listed in Section 2.1.1, an energy balance is produced on that surface. This balance can be represented by the equation: κ∂TSext ∂ n+˙ qconv,ext +˙ qSW +˙ qLW =0 (1) where  n is the outward normal vector to the roof external surface Sext ; κ is the conductivity of the material composing Sext , and TSext is the temperature on surface Sext ; ˙ qconv,ext is the intensity of convective heat flux between Sext and the ambiance air; ˙ qSW is the intensity of the solar radiation flux reaching Sext ; ˙ qLW represents the balance of thermal radiation between Sext and the sky and surroundings. 2.2.2. Absorbed Solar Radiation Calculation Regarding solar radiation, a relevant quantity for the computation of the thermal flux through the roof is the quantity of solar energy absorbed by the roof surface facing outward, that is computed here as: ˙ qSW =αSW ·Ib·cos(θ)·Ss Sroo f +Isd ·Frs +Igd ·Frg +Irn ·Frn,[W/m2](2) where αSW represents the solar absorptance coefficient of the roof’s outermost layer, θ denotes the solar beam’s angle of incidence on the roof, Ib is the intensity of the normal direct solar radiation, Ss is the sunlit area of the external roof surface, Sroo f is the entire roof area, Isd and Igd are the reflected diffuse solar radiation intensity from the sky and the ground, Frs is the view factor roof-sky, Frg is the view factor roof-ground, Irn represents the intensity of radiation reflected by the nearby buildings or any other vertical object such as trees, and Frn represents the view factor between the roof and the neighboring objects. When there are no structures or shading elements surpassing the specified roof in height, Frs and Frg are given by Frs =1+cos(φ) 2,Frg =1−cos(φ) 2 where φ is the angle that defines the tilt of the roof plane relative to the horizontal plane. In the case of an unshaded horizontal flat roof, φis equal to 0 and Equation (2) becomes ˙ qSW =αSW ·IH,[W/m2], (3) where IH is the intensity of the global horizontal solar radiation reaching the roof that is given by IH=Ib·cos(θ) + Isd. (4) Buildings 2024,14, 88 7 of 23 2.2.3. Long-Wave Radiative Exchange with the Sky The long-wave radiative exchange between the external roof surface and the sky is calculated using the expression ˙ qLW =˙ QLW sky −˙ QLWw where ˙ QLW w is the intensity of the thermal long-wave radiation emitted by the external roof surface and ˙ QLW sky is the sky downwelling long-wave radiation. ˙ QLW wis calculated using the Stefan–Boltzmann law: ˙ QLW w=ϵwσT4(5) where ϵw and T are the emissivity and the temperature in Kelvin degrees of the external surface of the roof, and σ is the Stefan–Boltzmann constant given by σ= 5.67 · 10−8[W/m2K4]. To compute the sky downwelling long-wave radiation ˙ QLW sky , following [ 21 , 22 ], the correlation used is: ˙ QLW sky =ϵskyσT4 ext, (6) where ϵsky is the sky emissivity and Text is the ambiance dry-bulb temperature in Kelvin degrees. From the same references [21,22], ϵsky is computed by ϵsky = (0.787 +0.764 ln(Tdp 273))(1+224 104n−35 104n2+28 105n3) where n is the opaque sky cover in tenths and Tdp is the dew point temperature in kelvin degrees. This approach is the same used by some well-known software of Building Energy Simulation as Energy Plus [23]. 2.2.4. Heat Exchange between the Roof and the Ambiance Air The heat exchange between the roof and the ambiance air, ˙ qconv,ext in Equation (1), is one of the processes that most affects the thermal behavior of the roof, hence the need to explore ways to ensure the accuracy of the calculation of this process. In this work, two ways of estimating ˙ qconv,ext have been analyzed. The first is a typical approach based in the use of convective heat transfer coefficients hconv,ext . The coefficient hconv,ext used here is based in the work of Hagishima and Tanimoto [ 24 ] and was obtained from experimental measurements on building roofs. The obtained correlation was hc,ext =8.18 +2.28VR[W/m2K], (7) where VR expresses the wind velocity above the roof, measured in meters per second. Then, the convective heat flux is given by ˙ qext =hc,ext(Text −TSext ), [W/m2]. (8) In the second approach used to estimate the heat exchange between the roof and the ambiance air, no external convective heat transfer coefficient has been used. Instead, the air flow over the roof has been modeled using the Navier–Stokes thermodynamic equations together with a turbulence modeling using the well-known κ−ε model. From these equations, the velocity and temperature of the air in the boundary layer adjacent to the outer surface have been determined. Then, the value thus calculated for the air temperature in the zone of the thermal boundary layer closest to the roof surface is the one used to determine the heat exchange ˙ qext. To carry out this modeling of the air flow over the roof, a parabolic air profile, used in energy performance of buildings [ 25 ], has been considered in the input of the calculation domain: Buildings 2024,14, 88 8 of 23 V(h) = Vrh hrγ (m/s) (9) In this equation, V(h) represents the wind velocity at height h , Vr denotes the wind speed measured at the reference altitude hr , and γ is a coefficient that varies depending on the local orographic and roughness characteristics. The remaining border conditions for air velocity are non-slip velocity on the outer roof surface, slip condition on the top of the domain, and finally, free outflow in the outlet boundary surface. 2.2.5. Heat Conduction through the Roof The conduction of heat through the roof can be modeled as a specific case of diffusion through a multilayer wall [ 26 ] and employing boundary conditions as defined by the energy balance equations for both the exterior and interior surfaces of the roof. The boundary conditions for the roof outer surface are described in Equation (1) and Section 2.2.4. Regarding the roof’s interior surface, when conducting the energy balance analysis for this surface, a mixed convective-radiative transfer coefficient hconv,rad was used. Here, following the values recommended by [ 27 ], the values considered for this coefficient were hconv,rad = 9.26 [W/m2K] for upward heat flux and hconv,rad = 6.13 [W/m2K] for downward heat flux. Finally, the model approximation for the simulation of the heat through the roof is the model for heat conduction through a multilayer wall introduced in [ 28 ], which is based on an approximation that takes into account specific continuity conditions between layers for temperature and heat flux. 2.3. Changes in Cool Roof Reflectivity Due to Aging It has been established in the previous literature [ 29 – 33 ] that cool coatings, based on paints or elastomeric materials, are affected by an aging effect that alters their solar reflectivity. The thermal performance of roofs is significantly impacted by this aging effect, as indicated in [ 6 ]. In this last work, the comparison between the heat flux through a roof considering the aging effect and the same roof without taking this effect into account showed a significant difference that can lead to erroneous estimates of energy consumption and the results of the economic cost effectiveness analysis of energy retrofit measures on roofs. Therefore, when calculating heat flux through roofs, this aging effect must be taken into account and included in its energy calculation to draw reliable conclusions. In conclusion, to simulate realistic conditions, the aging effect must be considered to draw accurate conclusions with respect to the energy and economic outcomes of the retrofitted roofs. To account in the energy calculations for this aging effect, the first stage is to establish the pattern of aging. In [ 32 ], it was shown that for all types of reflective roof coatings tested, in the early two years after installation, roughly 95% of aging happened, with 98% occurring within the first three years after installation; similarly, research has demonstrated that when considering unwashed cool roof coatings on various substrates, there is typically a decrease in initial solar reflectivity of approximately 20–25% within the first few months to one year, with minimal alterations thereafter, and substrate type typically has limited impact. On the other hand, Bretz and Akbary [ 33 ] found that the majority of the decline in solar reflectivity takes place within the initial year, potentially even within the first few months, and then the value of solar reflectivity tends to remain stable. Eilert [ 34 ] also illustrated that the decline in solar reflectivity of white roofs is in the order of 10–30% and the greatest decrease typically occurs during the first year. Based on the field survey [ 32 ], the recommendation is to perform energy calculations using reflectivity values aged for a minimum of one year, which usually range from 75% to 80% of the initial values. Buildings 2024,14, 88 9 of 23 A similar conclusion was reached in [ 29 ]. The study’s field measurements yielded results indicating a decrease in solar reflectance ranging from 19% to 25% for various cool paints. In this study, it was also noted that the aging of the cool coating layer has a minimal impact on its thermal reflectivity. On the other hand, field measurements [ 32 , 33 ] suggest that periodic washing can reinstate the original reflectivity values to 90–100%. Nonetheless, as indicated by the author of this field research, the use of roof washing as a maintenance strategy for cool-coated roof surfaces is not a cost-effective approach for retaining or renewing solar-reflectance values, especially given the expectation that most solar reflectance loss will reoccur within three to six months. While washing can typically renew most of the solar reflectivity, especially during the early aging years, the effects are temporary (typically for three to six months) and deliver limited economic benefits. According to the consensus in most of the studies we have examined, the aging trend considered for the cool roof coating is as follows: during the first year, there is a reduction in solar reflectivity amounting to 20% of its initial value, with the majority occurring in the initial months of the year, and a further loss of 8.5% in the second year. A reduction of 0.9% is expected for the third year. Afterwards, the drop in reflectance tends to become steady [ 33 ], resulting in a total loss of 30% over the complete life cycle. Therefore, as indicated in [ 32 ], nearly 95% of the aging takes place within the initial two years, and approximately 98% occurs during the first three years after installation. On the other hand, when a wash is performed some years after installation, the relating literature supports that solar reflectivity is restored to 90% of the initial value. Subsequently, we consider the same pattern observed after the initial application of the cool coating. The solar reflectivity loss considered in this work as a result of the aging effect is estimated following the aforementioned aging patterns. In Figure 4, the estimated percentage of reflectivity loss for each year is shown. 0 5 10 15 20 25 Year 1 Year 2 Year 3 Rest of years Reflectivity loss in % Aging Pattern: Yearly reflectivity loss Figure 4. Pattern of solar yearly reflectivity loss in %. 2.4. Roof Energy Calculation Case Buildings In this study, we considered a typical building from the social housing edified in Seville before 1979. The analyzed building belongs to a social housing development named Polígono de San Pablo, built in the city of Seville, Spain, in the decade of the 1960s. This development showcases the typical construction style seen in social housing throughout this era, where the absence of energy insulation measures is a prominent feature. The roofs, as shown in Figure 2, are of the flat type. The development is made up of equal height buildings, and there are no adjacent structures of superior elevation that could cause shading over the roofs analyzed. Thus, the solar radiation flux reaching the roofs can be described by Equation (3). Buildings 2024,14, 88 16 of 23 In Figure 7a, the yearly heating, cooling, and total loads by m 2 of retrofitted roof are shown for the case of no washing of the cool coating. It can be observed that as a result of the high initial values of the cool-coating solar reflectivity, the values of the heating loads are higher in the first two years than for the remaining years due to the solar gain penalty; on the contrary, for the first two years, the cooling loads are lower than for the remaining years for the same reason. Regarding the total loads, this opposing behavior of the cooling and heating loads produces a final result that must be estimated considering the effect on the loads of the aging pattern. For the case study considered, the results depict a trend where total loads are notably higher in the first two years and then maintain a stable course in the remaining years. It should be noted that the heating loads in the present case study are higher than the cooling loads for the whole LCCA time span, in line with the effect that the high solar reflectivity produces in the thermal flux through the roof. In Figure 7b, the yearly heating, cooling and total loads by m 2 of retrofitted roof are shown for the case of a periodic quinquennial wash of the cool coating. The first observation that can be made from this figure is how the quinquennial washing of the roof produces a cyclic behavior of the loads, which is very similar for each five-year period between two consecutive washes. As can be seen, the effect of the cool paint on decreasing solar gain produces lower values for the cooling loads than for the heating loads throughout the 20 years of the considered life-cycle time span. It is worth noting that when the solar reflectivity of the cool paint reaches its highest values, that is, in the initial year, and then, after the quinquennial washing, years 6, 11, and 16, the cooling load reaches its minimum values; after each of these years, cooling loads are gradually increasing in each time interval between two consecutive washings, in line with the increasing loss of solar reflectivity produced by the aging effect of the cool paint. For the heating load, the pattern is just the opposite: when the solar reflectivity is maximum in years 1, 6, 11, and 16, the heating loads are maximum in accordance with the lowest values of solar gain; then, in the following years, the heating load follows a decreasing pattern produced by the aging effect that causes a loss of reflectivity and an increase in solar gain. This opposing behavior in the cooling and heating loads produces a certain balance in all the years except for the initial year of each inter-washing time period. In these initial years, the predominant effect is the reduction of solar gain, so that the rise in heating load is not balanced by the reduction in cooling load, resulting in an increase in the total load for those years. For the remaining years of each period between washings, it is observed that the variations in cooling and heating loads caused by the effect of the aging of the cold layer are approximately compensated for by each other, producing a very small variation of the loads over the different years of each period. On the other hand, the calculation of the heat flux for the reference roof gives a heating load equal to 28.72 kWh/m 2 and a cooling load equal to 38.32 kWh/m 2 , which implies a total load equal to 67.04 kWh/m 2 for every year of the LCCA span time. By comparing these values with the loads for the retrofitted roof shown in Figures 7and 8, it can be stated that the heating, cooling, and total loads for the retrofitted roof have lower values than the same loads for the reference roof, and this is. the case for all the years of the LCCA time span and for the two washing protocols considered; consequently, it can be stated that the retrofitted roof yields positive energy savings for all the years of the considered LCCA time span, as can be seen in Figure 9. In Figure 8, the loads for the entire LCCA time span are shown for the reference and retrofitted roofs. According to Figure 7and the subsequent discussion for heating and cooling loads and thus for the total load, the retrofitted roof exhibits lower values than the reference roof and, as can be appreciated in the figure, the highest reduction is achieved for the cooling loads. In Table 4, the values of the different loads for the LCCA span are shown for the retrofitted and reference roofs. Buildings 2024,14, 88 17 of 23 Table 4. Life-cycle loads and energy savings kWh/m2. Heating Load Cooling Load Total Load Total Energy Saving Reference roof 574.35 766.56 1340.91 - Retrofitted roof (No wash) 269.23 103.03 365.29 975.62 Retrofitted roof (Quinq. wash) 280.23 90.27 370.51 970.40 0 2 4 6 8 10 12 14 16 18 20 22 12345678910 11 12 13 14 15 16 17 18 19 20 Load kWh/m2 Year Heating Load Cooling Load Total Load (a) 0 2 4 6 8 10 12 14 16 18 20 22 12345678910 11 12 13 14 15 16 17 18 19 20 Load kWh/m2 Year Heating Load Cooling Load Total Load (b) Figure 7. Yearly heating, cooling, and total loads for the retrofitted roof with (a) no wash of the cool coating; (b) quinquennial wash of the cool coating. 0 200 400 600 800 1000 1200 1400 Heating Cooling Total Load kWh/m2 LCA Loads. No wash. Retrofitted roof Reference roof (a) 0 200 400 600 800 1000 1200 1400 Heating Cooling Total Load kWh/m2 LCA Loads. Quinquennial Wash Retrofitted roof Reference roof (b) Figure 8. LC heating, cooling, and total loads for the reference and retrofitted roofs with (a) no wash of the cool coating; (b) quinquennial wash of the cool coating. 0 5 10 15 20 25 30 35 40 45 50 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 Energy Saving kWh/m2 Year Load Savings. No Wash Heating load savings Cooling load savings Total load savings (a) 0 5 10 15 20 25 30 35 40 45 50 12345678910 11 12 13 14 15 16 17 18 19 20 Energy Saving kWh/m2 Year Load Savings. Quinquennial Wash Heating load savings Cooling load savings Total load savings (b) Figure 9. Yearly heating, cooling, and total energy savings for the retrofitted and the reference roofs for (a) no wash of the cool coating; (b) quinquennial wash of the cool coating. The energy savings for each specific load are defined as the difference between the load for the reference roof and the load for the retrofitted roof. Thus, positive energy savings mean that the load on the reference roof is higher than the same load on the retrofitted roof. As can be observed in Table 4, the retrofitted roof has positive or true total energy savings Buildings 2024,14, 88 18 of 23 when compared to the reference case. In Figure 9, the heating, cooling, and total savings are displayed for each year of the LCCA span time. It can be noted that the case of periodic quinquennial wash of the cool coating provides slightly better results with respect to the total load and energy savings compared to the case of no wash. According to the above discussion, for the case of no wash of the cool coating, Figure 9a, the lowest values for the energy savings are obtained in the two initial years and then tend to stabilize for the remaining years. It should be noted that the savings for cooling load are much higher than the savings for heating load. In Figure 9b, the load savings for the case of a quinquennial wash of the cool coating are shown. It can be observed that the lowest values for the energy savings are obtained in the two initial years and then in the years in which the washing is carried out due to the penalty in the solar gain produced by the high values of solar reflectivity. For the remaining years of each period, the decrease in the solar reflectivity produced by the aging lowers the solar reflectivity and, as can be seen in the figure, this makes the total load go down. Likewise, in Figure 9, the greatest effect in producing savings is observed for the cooling load when compared to the heating load, as a result of the decision to install a cool paint with very reduced solar reflectivity. Finally, in Table 5, the LCCA energy savings are shown for all housing in every district of the neighborhood and the neighborhood as a whole. Table 5. Life cycle energy savings for the districts and neighborhood as a whole. District No Wash Quinquennial Wash A 21,796,326.4 kWh 21,679,684.1 kWh B 22,781,702.6 kWh 22,659,787.1 kWh C 24,696,844.7 kWh 24,564,680.3 kWh D 22,923,167.5 kWh 22,800,494.9 kWh E 16,911,397.1 kWh 16,820,896.3 kWh All 109,109.44 mWh 108,525.54 [] mWh Taking into account the assumed SEER and SCOP coefficients, the savings in thermal loads shown in Table 5are equivalent to a total reduction in energy consumption of 32,500 mWh for the entire neighborhood and the entire life cycle, which is equivalent to a 72% reduction in energy consumption to achieve indoor thermal comfort. This value of energy consumption decrease implies a total reduction in CO2emissions of 4488.31 tons. 3.2. LCCA Results In this section, the net savings and payback periods are used as performance indicators to perform the LCCA. Due to the investment in refurbishment made compared to the reference case, the NCS and PB are assessed under the economic framework described previously and considering the impact on energy loads of the effect of aging as described previously. In Table 6, the monetary net savings per unit of roof surface area, NCS, and the payback period, PB, are shown for the two maintenance protocols considered: no powerful wash during the entire LCCA time period and a periodic quinquennial wash. Additionally, net savings are presented for the roof with three standard surface areas in the framework of social housing, that is, roof areas equal to 60, 70, and 80 m 2 : the usual range of roof surfaces for this kind of dwelling. Buildings 2024,14, 88 19 of 23 Table 6. Life-cycle monetary savings and associated payback periods. No Wash NCS [e]for roof surface i dr NCS [e/m2]PB [years] 60 m270 m280 m2 0.015 0.01 57.26 7.69 3435.6 4008.2 4580.8 0.03 0.015 64.96 7.15 3897.6 4547.2 5196.8 0.06 0.03 77.18 6.84 4630.8 5402.6 6174.4 Quinquennial Wash NCS [e]for roof surface i dr NCS [e/m2]PB [years] 60 m270 m280 m2 0.015 0.01 52.45 8.12 3147 3671.5 4196 0.03 0.015 60.03 7.42 3601.8 4202.1 4802.4 0.06 0.03 72.026 6.93 4321.56 5041.82 5762.08 As can be seen in Table 6, the proposed retrofitting measures are cost-efficient for all the cases analyzed. However, it can be stated that the results obtained for the no-wash maintenance protocols are better than those obtained for the quinquennial washing, with higher values of monetary savings and thus shorter PB periods for the no wash case. It should be highlighted that the payback periods for all the cases are not long and range between 6.84 and 8.12 years. These can be considered reasonable time intervals to recover the investment made in the retrofitting. Regarding the economic indicators, it can be observed that the proposed combined retrofit measure yields the highest monetary savings for high values of the energy inflation index and the monetary discount rate represented here by i = 6% and dr = 3%. Taking into consideration the present economic situation characterized by very high energy price growth and very high inflation rates, it can be concluded that, financially speaking, the proposed retrofitting measure is highly effective. In the same table, net monetary savings are presented for three typical roof areas of social dwellings. As can be observed, the value of these savings is relevant, and their impact on the household economy of regular residents of social housing, usually characterized by low incomes, can be described as of great significance and with a high potential to achieve indoor comfort and health conditions and reduce the high rates of energy poverty found among the inhabitants of this type of housing. Finally, in Table 7, the monetary savings for the whole LCCA time span for all the retrofitted dwellings in each district and for the entire neighborhood are shown for all the different economic scenarios of energy inflation and discount rate considered. Table 7. Net savings [ e ] for the districts and the entire neighborhood. The values of i and dr are given in %. No Wash Quinquennial Wash District i = 1.5, d=1 i = 1, d = 1.5 i = 6, d=3 i = 1.5, d=1 i = 1, d = 1.5 i = 6, d=3 A 1,279,245.66 1,451,271.36 1,724,278.38 1,171,785.45 1,341,130.23 1,609,222.23 B 1,337,078.26 1,516,880.96 1,802,230.18 1,224,759.95 1,401,760.53 1,681,972.53 C 1,449,479.64 1,644,397.44 1,953,734.52 1,327,719.30 1,519,599.42 1,823,367.42 D 1,345,380.96 1,526,300.16 1,813,421.28 1,232,365.20 1,410,464.88 1,692,416.88 E 992,544.84 1,126,016.64 1,337,838.12 909,168.30 1,040,560.02 1,248,568.02 All 6,403,729.36 7,264,866.56 8,631,502.48 5,865,798.20 6,713,515.08 8,055,547.08 As can be observed, the quantities saved during the analysis period, the life-cycle time span, are significant for all the analyzed scenarios in terms of both economy and maintenance protocols. It is observed that for the entire neighborhood, quantities saved Buildings 2024,14, 88 20 of 23 range from e 6.4 million to over e 8.6 million in the no wash case, depending on the economic scenario. 4. Conclusions In this work, the Aura Strategy as an intervention methodology to find global solutions to issues in outdated neighborhoods has been visualized through the analysis of a constructive solution to improve the energy performance of the roofing of buildings applied to the case study of an energy obsolete residential neighborhood in the city of Seville, Spain. This architectural solution impacts 3 out of the 4 lines of intervention: Health and Comfort, Materiality, Cultural Identity, and Energy and Conditioning that the Aura Strategy proposes as the focus of all urban regeneration interventions. 1. Energy and Conditioning: the effectiveness of the proposed retrofit measure, which combines a cold coating with insulation to reduce energy loads and achieve indoor comfort in the affected dwellings, is confirmed. For the LCCA time span, the load reduction reaches 975.62 kWh/m 2 for the maintenance protocol without washing and 970.40 kWh/m 2 for the maintenance protocol with five-yearly washing. When these savings are quantified for all homes with roofs in the neighborhood, the results are 109,109.44 and 108,525.54 mWh, respectively. These thermal load reduction results indicate a 72% reduction in energy consumption to achieve indoor thermal comfort. This load reduction is equivalent to a savings of almost 4,488 tons of greenhouse gas emissions across the district and over the entire lifetime of the applied roof retrofit measure. Therefore, it can be concluded that the implementation of the proposed retrofit measure to reduce energy consumption leads to significant energy saving capacity. 2. Materiality: From a financial perspective, the Life Cycle Cost Analysis provides net economic cost savings for the entire analysis period. In the case of the Nowash maintenance protocol, these range between 57.26 and 77.18 em2 per dwelling, depending on the economic scenario, with return-on-investment periods between 7.69 and 6.84 years. In the case of the Quinquennial Wash maintenance protocol, net savings are between 52.45 and 72.03 e/m2 and return-on-investment periods are between 8.12 and 6.93 years. This allows us to establish the cost effectiveness of the proposed retrofit measure for family dwellings and homeowners. If all affected homes in the neighborhood are considered, financial savings for the LCCA time span range from e 5,865,798.20 to e 8,055,547.08 in the case of the quinquennial wash maintenance protocol, and from e 6,403,729.36 to e 8,631,502.48 in the case of the no-wash maintenance protocol. Therefore, financially speaking, the economic viability of the proposed retrofitting is confirmed, as well as the significant savings that its implementation implies for individual households and for the neighborhood as a whole. 3. Health and Comfort: The applied solution, by incorporating thermal insulation in the roof, improves indoor comfort conditions in the affected dwellings. The proposal, in addition to the consequent reduction of energy expenditure and consequently the reduction of economic expenditure, implies the reduction of energy poverty levels, the improvement of indoor living conditions, and their repercussions on health and well-being [ 55 ]. It also implies a very positive effect on the reduction of greenhouse gas emissions. In short, this retrofit proposal fulfills the premises established by the Aura Strategy: the regeneration of obsolete neighborhoods through specific energy retrofit interventions that offer global benefits to the population of the case study, as described in this article. In turn, this has a direct impact on people’s health, especially among elderly residents in the neighborhood, and on the fight against climate change. To put these figures in context, it should be highlighted that in 2018, the annual income per capita in the Polígono de San Pablo was e 8128.86 while the household income was e 19,973.84 (Source: National Institute of Statistics, Spain). Thus, savings would constitute a significant percentage of the economic capacity of residents of the neighborhood. Buildings 2024,14, 88 21 of 23 The energy and economic results obtained from the numerical modeling at the roof building level are consistent with the previous literature. On the other hand, the specific solution adopted for roof retrofitting in the research carried out has benefited from previous studies carried out by the authors, which has allowed the high levels of energy savings presented in this study that have contributed, in the context of the Aura Strategy, to the finding of significant energy and monetary savings at the neighborhood level. The main limitation of this study was the scarcity of social information related to the evaluation of the application of the research results by all parties involved in society, such as tenants, municipalities, state governments and other subjects, both private and public, with the possibility of influencing the decision making process leading to the implementation of the rehabilitation measures described above, especially the subsidization of the necessary investments. Therefore, the possibility of extending the present research to the study of the social response to the type of strategies proposed in the present investigation represents an opportunity for new studies that also need to be addressed. Finally, the study focuses on the analysis of a specific constructive solution to improve the thermal performance of the roof of a typical building. The results obtained with this initial approach have certain limitations, suggesting the possibility of extending the research carried out by comparing it with other construction alternatives. Author Contributions: Conceptualization, methodology, software, formal analysis, investigation, writing—original draft preparation, writing—review and editing, C.A.D.-T., H.D.-T., M.H.-V., J.R.-F. and R.H.-L. All authors have read and agreed to the published version of the manuscript. Funding: This article is included in the project “Aplicación directa de la Estrategia Aura del Equipo Solar Decathlon–U.S., en rehabilitación de barriadas obsoletas andaluzas” granted by the Ministry of Development, Infrastructure and Territorial Planning of the Local Andalusian Government (Spain), with ref. US.20–11, but for its production no economic financing has been received. Data Availability Statement: Data are available under request to the corresponding author. The data are not publicly available due to logistic storage issues. Conflicts of Interest: The authors declare no conflict of interest. References 1. Herrera-Limones, R.; León-Rodríguez, Á.; López-Escamilla, Á. Solar Decathlon Latin America and Caribbean: Comfort and the Balance between Passive and Active Design. Sustainability 2019,11, 3498. [CrossRef] 2. Herrera-Limones, R.; Hernández-Valencia, M.; Roa-Fernández, J. Urban regeneration through retrofitting social housing: The AURA 3.1 prototype. J. Hous. 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