3.1. Qualitative Aspects
As highlighted in
Table 5, the resulting musts exhibit enological characteristics that are both comparable and suitable for high-quality winemaking. This aligns with the criteria outlined by Ribéreau-Gayon P. et al., 2005 [
24].
A significant difference observed was the lower ethanol content in the must obtained from grapes cooled with CO2 compared to that from grapes processed using the heat exchanger system. In the latter case, the static clarification phase (conducted at room temperature in this trial) initiated spontaneous fermentation, leading to the development of 0.96% vol. ethanol, compared to 0.26% vol. recorded with the direct CO2 cooling system. This difference is likely due to the faster cooling and deoxygenation of the must achieved with CO2, which slowed the activity of indigenous yeasts present on the grape surface that inoculate the must.
This result warrants further investigation, as the clarification phase plays a crucial role in the quality of the must and the resulting wine. In many cases, it is carried out via static decantation at low temperatures [
25]. If the mildly inhibitory effect of CO
2 treatment is confirmed, it could allow for the use of slightly higher temperatures during clarification, potentially leading to energy savings due to the reduced amount of CO
2 required for grape cryo-cooling.
In line with the observed ethanol differences, must derived from the use of CO2 contained a higher sugar concentration: 198.68 g/L compared to 168.58 g/L for the traditional system. Differences were also noted in the color and hue of the must, which were more pronounced with CO2 cooling. The rapid cooling achieved with CO2 facilitated greater extraction of anthocyanin compounds during the subsequent pressing phase.
This suggests that direct CO2 cooling not only enhances heat exchange but also promotes the extraction of compounds of interest from the solid parts of the grapes. This characteristic points to broader potential applications for CO2-based cooling, though further studies are needed to evaluate these effects in depth. Indeed, despite the higher overall energy consumption of CO2-based cooling due to the energy required for CO2 production, we observed a significantly improved quality of must obtained through this process, which may substantially impact the assessment of its environmental footprint.
3.2. Tests with Heat Exchanger
Figure 5 illustrates the trend over time of the active power associated with the cooling water pump. The short measurement duration is due to the pump operating cyclically at a constant flow rate with a power factor not lower than 0.94 and absorbed power ranging between 4.78 kW and 4.87 kW with an average value of 4.84 kW (
Table 6).
Figure 6 shows the trend of active power for the chiller, which has a power factor of 0.8, considered acceptable for a refrigeration unit serving multiple winery utilities. In this case, the measurement was stopped once steady-state conditions were reached, corresponding to an average absorbed active power of 62.8 kW (
Table 6). The active power of the single-screw pump pushing the crushed grapes into the heat exchanger was 11.1 kW on average.
It is noted that the active power absorption of the whole crushed grapes cooling line with indirect heat exchange is mainly due to the water cooler (chiller); in this case, the relatively low power factor and the high active power absorption are certainly due to the use of the refrigeration unit in a very wide ambient temperature range, leading to a high condensation temperature. This is a typical limitation of the regions of Southern Italy, where the grape harvest takes place with a still warm climate, which causes the cooler compressor to operate with low efficiency and high electrical consumption.
In this case, energy calculations must consider only the steady-state condition over the entire trial duration of 27 min. Accordingly, the energy consumption amounts to 2.2 kWh for the refrigerated water pump, 5.0 kWh for the single-screw pump and 28.3 kWh for the water chiller, resulting in a total energy consumption of 35.5 kWh. Considering an average cost of 0.20 EUR/kWh, the energy cost for the trial is approximately EUR 7.10, which is negligible relative to the final wine’s production cost. Finally, considering the processing of 9000 kg of crushed and destemmed grapes (mash), the specific energy consumption is calculated at 14.2 kJ/kgmash (
Table 6).
3.3. Experiments with CO2
Figure 7 illustrates the time-dependent behavior of the active power associated with the refrigeration system employing direct CO
2 injection. The electrical consumption is primarily attributable to the operation of the single-screw pump, which transfers the CO
2-cooled crushed grapes to the press. The remaining electrical load, approximately 78–82.0 W, is due to the instrumentation integrated into the system.
The single-screw pump operates intermittently, activating when the crushed grapes reach the maximum level in the loading hopper. This intermittent operation accounts for the periodic increases in active electrical power from 0.08 kW to 4.5 kW with an average power of 2.2 kW. Of course, also in this case, the active power of the single-screw pump pushing the crushed grapes into the CO2 injection system was 11.1 kW on average.
The power factor remains nearly equal to 1 during the pump’s operation and obviously drops to 0.25 during other intervals (
Table 7). In this experiment, the measurements were concluded upon processing the entire quantity of crushed and destemmed grape mash (15,000 kg). In this case, the absorbed power does not depend on ambient conditions.
The total energy consumption for the process was 11.1 kWh, with a corresponding energy cost of EUR 2.22 (
Table 7). Moreover, it is important to note that both energy consumption and cost must account for producing CO
2 by an external supplier, which is then sold to the winery. The cost of bulk CO
2, including transportation and storage, ranges from 0.6 EUR/kgCO
2 to 0.75 EUR/kgCO
2, with temporary price spikes during shortages reaching up to 10 EUR/kgCO
2. Given that 800 kg of CO
2 was used, the CO
2 cost adds an average of 0.75 EUR/kgCO
2, amounting to a total cost of EUR 600. This corresponds to a unit cost of 0.04 EUR/kg of crushed and destemmed grapes (mash), resulting in a negligible increase in the final wine production cost. Therefore, from an economic standpoint, the impact on the final cost is minimal and the choice between the two systems cannot be based solely on economic considerations. As said in the previous paragraph, the quality of CO
2-refrigerated mash was much better than that obtained through the traditional heat exchanger refrigeration process, and this leads again to choosing the CO
2-refrigerated mash instead of the traditional one.
But, when using CO
2, the energy balance must account for the energy required to capture, liquefy and store the gas, which must also meet the purity standards necessary for food-grade applications. According to the literature, the energy consumption for capturing and purifying CO
2 is globally (sum of thermal and electric consumption) 2250 kJ/kgCO
2 according to Zheng, Y.; Gao, L., 2023 [
26], 3900 kJ/kgCO
2 and 432 kJ/kgCO
2 (respectively, thermal and electric consumption) according to Haaf M. et al., 2020 [
27]; the energy required for liquefaction and storage amounts to 288 kJ/kgCO
2 according to Chen, F.; Morosuk, T., 2021 [
28]. Considering only the liquefaction process, when scaled to the unit mass of processed must, this corresponds to an energy consumption of 15.4 kJ/kg of crushed grapes, which is slightly over the energy consumption of the heat exchanger-based system. The capture process is of course about 10 times more energy-hungry.