Following the shape and functional analysis, smart locks are implemented in the case study office building as an enabling technology. These locks facilitate the operation models previously identified, allowing for the partial shutdown of building functions. The results, including energy savings and environmental impact, are detailed in this section. The findings are combined to provide a final assessment of energy, carbon and cost savings and the return time of the investment in terms of carbon emissions.
4.1. Building Savings Assessments
As a first outcome of the study, this section delves into the essential parameters for designing a compartmentation strategy: the occupancy profiles and the internal gains, the location and space function of the building rooms, and the weekly trends in energy consumption. Comprehension of the relationship between the bespoke factors is essential for the development of guidelines for future applications of the study. The best closure layout strategy is defined daily; the savings in terms of costs and carbon emissions are quantified demonstrating the effectiveness of the proposed methodology for a real office building.
The baseline building global Primary Energy consumptions and related costs, following the proposed methodology, are reported in
Table 8.
The share of energy use per type is detailed in
Figure 7.
The four hemi-floors are comparable both in terms of space, people and annual savings, which range from a minimum of 9.1% for closure SF1 to a maximum of 12.2% for closure SF2 considering ISO 17772-2 [
53].
Figure 8 shows the annual savings for each closure strategy for both standards and assuming an annual closure for each hemi-floor for the sake of comparison. The daily savings values should be considered to maximize the savings potential of the closure.
A dynamic and remote-controlled lock gives the possibility of exploiting the building characteristics to maximize savings, which were first presented in
Figure 8 considering the same hemi-floor as constantly closed during the year. In
Figure 9, the variability of daily savings during heating and cooling seasons is presented. Considering the results obtained with ISO 18523-1 [
54], the savings due to the closure of any hemi-floor during the cooling season are always higher than the savings recorded during the heating season: the extended occupancy schedule has a high impact on the simulated internal loads for ISO 18523-1 [
54], resulting in an energy-expensive cooling season.
Moreover, the closure strategies related to south wing hemi-floors obtain a wider range of savings, reaching a difference in daily savings of 0.91 kWh/m2 for SF2. The lowest energy savings, gained when closing the south wing second floor (SF2), are scored on the 28th of April (0.31 kWh/m2), and the maximum daily savings on the 3rd of August (1.22 kWh/m2): the increased internal loads contribute to thermal comfort during midseason, while they should be balanced during summer.
Regarding ISO 17772-2 [
53], the north wing average savings are always higher during the heating season. The south ground hemi-floor follows the same trend, having an average possible saving of 0.66 kWh/m
2 during the heating season and 0.60 kWh/m
2 during the cooling season. The reason for the differences in trend between the south ground floor and the other south floors can be found in the number of exposed surfaces and their stratigraphy. In general, a performative closure strategy should be defined daily.
Due to the absence of real data on occupancy, the best closure is defined as the maximization of energy savings without consideration of the number of available/needed seats. The distribution is studied for the two standards that are considered as minimum and maximum occupancy. The chart is created by combining the results of the single simulations (“Best closure” simulation). Clearly, mid-season registers the lowest benefit from the closing strategy while, in extreme temperature periods, the savings are higher, reaching a maximum of 2.64 kWh/m2 on the 3rd of August; a similar value of 2.54 kWh/m2 can be saved by closing south wing ground floor (SF0) for the 5th of January.
Regarding simulated energy consumption, it is possible to determine daily closures of the hemi-floor which leads to the greatest energy savings. The following graph (
Figure 10) shows the maximum achievable energy savings based on the time of year and usage profile, compared to the two standards analyzed, which were selected to represent the building’s highest and lowest occupancy levels. The chart is created by combining the results of the single simulations (“Best closure” simulation) per day.
The corresponding best hemi-floor closure for each day of the year is reported in
Figure 11. Considering ISO 18523-1 [
54], the optimization strategy is dominated by the closure of SF0, both in the heating and cooling seasons.
Appendix A provides some insights into the external conduction losses of the South ground floor, which are responsible for the high consumption, or savings when closed, of this hemi-floor. Instead, ISO 17772-2 [
53] model gives a mixed closure distribution: the two ground hemi-floor closures alternate during the cooling season, while SF2 is prevalent in summer due to the high exposure to solar radiation of this hemi-floor.
Each year the defined configuration leads to a total amount of savings of around 13% for both standards. The total savings are reported in
Table 9 in terms of primary energy.
These savings can be obtained with an 89% occupancy, i.e., 25 people at home, when 237 people account for the full capacity of the building (
Table 10). In conclusion, the annual Energy Use per Person is computed considering an 89% occupancy distributed across the whole building and 89% occupancy considering the best closure distribution previously highlighted.
During the closure, the EUP decreases by 10% with respect to the same occupancy without a people management strategy.
4.2. Cumulative Energy Demand, GWP and Carbon Footprint over the Life Cycle
4.2.1. Cumulative Energy Demand and GWP of Conventional Locking System vs. Smart Lock
From the primary data collected and the elaboration of the inventory of energy, materials and waste tracked at the manufacturing stage, the LCA of the two main locking devices, the mechanical cylinder and the electronic lock, were performed and the results were compared. As shown in
Figure 12, the production from cradle to gate of the mechanical cylinder generates an emission of 2.3 kg CO
2-eq per piece. This includes the production of all mechanical components, keys (three copies per device) and packaging.
Nearly 70% of the carbon emission is allocated to the production of the metallic cylinder, where brass processing is the major contribution to the share. An additional 15% of carbon emission is generated by the key production and waste generated by steel processing. Finally, the packaging used to store and sell the product contributes an additional 15% of the total emission, with a large contribution of carton paper used for the product cover. Since brass processing is dominant, and a large amount of residue is generated during production, the recovery of brass at the end of the life of the product is an essential step to be tackled in order to implement circularity in the value chain and reduce the overall carbon footprint of the device.
In contrast, the electronic device used as a smart locking system achieves a total emission of 5.7 kg CO2-eq, which is around 2.5-fold the carbon intensity obtained from the mechanical cylinder. The result is heavily influenced by the large presence of electronic components, with production involving carbon-intensive processes and assemblies. The contribution of the electronic components is dominant, with nearly 3.2 kgCO2-eq emitted, which corresponds to 66% of the total share. More than 47% of the carbon emission is caused by the rotor, which dominates the share of the electronic components, along with the sole electronic board, which contributes to 16% of the total share. The mechanical processes for the fabrication of the mechanical components play a minor role, with a contribution equal to 28%. Finally, a marginal contribution is registered for the packaging, with a share of 5%.
In
Figure 13 the results of cumulative energy demand (CED) are shown. For both cases, the contribution of non-renewable energy is dominant and much larger (almost 5-fold more in the case of the smart lock) than that caused by renewable energy.
In the case of the conventional lock, the dominant contribution, both renewable and non-renewable, is caused by mechanical components (between 69–71% of the share), while both packaging and key production contribute to an additional 14–16% each. In contrast, for smart lock production, the main energy need is registered for the electronic component’s fabrication, which requires nearly 16 kWh of non-renewable energy and roughly 2.5 kWh of renewable. Next are the mechanical components, with a relative share of 25–20%, and finally the packaging, with a marginal contribution of 4–10% to the global cumulative energy demand.
4.2.2. Carbon Footprint of Conventional Locking System vs. Smart Lock
At the building scale case, the carbon footprint of all devices and connections needed to run the locking system was estimated and carbon emissions summed up for carbon savings from the operational energy saved by the monthly flow optimization of users, according to the two affluence standard scenarios, assumed and described in
Section 3.4.1. The cumulative embodied carbon and the cumulative operational carbon saved by implementing a smart lock system under a base device layout on the building case study are shown in
Figure 14. In the life cycle assessment carried out, four main time laps over 20 years of service life were evaluated. At year 1, i.e., time of installation, the only contribution is related to the embodied carbon of the installed components, which account for around 2 tons of CO
2-eq. After 5 years of usage, the carbon savings from operational energy optimization show a significative dominance, with around 196 tons of CO
2-eq saved in case of affluence according to ISO 18523-1 and around half-savings, equal to 82 tons of CO
2-eq in case of affluence according to ISO 17772-2. Even considering the maintenance operation of the management system, as well as the replacement of exhausted electronic components and batteries, the cumulative carbon savings increase nearly linearly at every step, with a total saving which increases in the case of ISO 18523-1 from 444 tons of CO
2-eq after 10 years of use to 940 tons of CO
2-eq after 20 years from the installation. Similarly, in the case of ISO 17772-2, the total cumulative savings increase from a range of 187 to nearly 400 tons of CO
2-eq in 10 years.
Finally, the cumulative carbon savings under the two alternative configurations, base and optimized, are compared and the results are visualized in
Figure 15. According to ISO 18523-1 [
54], moving from a base device layout, which consists of installing 69 smart locks in the building case study, to an optimized scenario, with a reduction to just 7 pieces, brings a carbon reduction equal to 0.66 tons of CO
2-eq at the time of installation. After 5 years, a marginal difference between the two layouts is registered, mainly due to the replacement of the batteries of the devices and the lower amount of electricity needed by the system. After 10 years from installation until the end of life, the gateways are assumed to be replaced with new ones, and this avoids emission in the case of the optimized device layout, with a relative saving of nearly 1.5 tons of CO
2-eq in the case of ISO 18523-1 and roughly 1.8 tons in the case of ISO 17772-2 [
53].