Next Article in Journal
Investigation and Improvement of Standard External Lightning Protection System: Industrial Case Study
Next Article in Special Issue
Enhancing PV Self-Consumption through Energy Communities in Heating-Dominated Climates
Previous Article in Journal
The Proposal of a New Tool for Condition Assessment of Medium Voltage Power Cable Lines
Previous Article in Special Issue
Hygrothermal and Acoustic Performance of Two Innovative Envelope Renovation Solutions Developed in the e-SAFE Project
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

The Effect of the Thermal Mass of the Building Envelope on Summer Overheating of Dwellings in a Temperate Climate

1
Faculty of Civil Engineering, Architecture and Environmental Engineering, University of Zielona Góra, 65-516 Zielona Góra, Poland
2
Faculty of Social Science, University of Zielona Góra, Wojska Polskiego 69 St., 65-762 Zielona Góra, Poland
*
Author to whom correspondence should be addressed.
Energies 2021, 14(14), 4117; https://doi.org/10.3390/en14144117
Submission received: 5 April 2021 / Revised: 15 June 2021 / Accepted: 6 July 2021 / Published: 8 July 2021
(This article belongs to the Special Issue Challenges and Research Trends of Building Energy Performance)

Abstract

:
The main objective of this paper is to demonstrate the effectiveness of increasing the thermal capacity of a residential building by using traditional building materials to reduce the risk of its excessive overheating during intense heat waves in a temperate climate. An additional objective is to show that the use of this single passive measure significantly reduces the risk of overheating in daytime rooms, but also, though to a much lesser extent, in bedrooms. Increasing the thermal mass of the room from light to a medium heavy reduced the average maximum daily temperature by 2.2 K during the first heat wave and by 2.6 K during the other two heat waves. The use of very heavy construction further reduced the average maximum temperature for the heat waves analyzed by 1.4 K , 1.2 K and 1.7 K , respectively, giving a total possible reduction in maximum daily temperatures in the range of 3.6 °C, 3.8 °C and 4.3 °C. A discussion of the influence of occupant behavior on the use of night ventilation and external blinds was carried out, finding a significant effect on the effectiveness of the use of both methods. The results of the study suggest that in temperate European countries, preserving residential construction methods with heavy envelopes and partitions could significantly reduce the risk of overheating in residential buildings over the next few decades, without the need for night ventilation or external blinds, whose effectiveness is highly dependent on individual occupant behavior.

1. Introduction

1.1. Effect of Global Warming on Outdoor Temperature in Europe

The occurrence of summer heat waves in temperate European countries has increased over the past few years, with a significant increase in both their frequency and duration, and in the height of maximum temperatures experienced. In 2018–2019, extreme high temperatures occurred in most of the temperate European countries. The highest summer temperature on record was in the United Kingdom in 2018 [1]. In a large part of Western Europe and Scandinavia, extreme high temperatures occurred in the last week of June 2019 [2]. In June and July 2019, historical records for the highest temperatures were set across France, Switzerland, Benelux, Germany, the United Kingdom, or northern Italy [2]. The probability of very high summer temperatures due to anthropogenic causes has increased by as much as 30 times [3]. Christidis et al. [1] estimate that in the UK the probability of days with temperatures above 40 °C is currently low, but without reductions in greenhouse gas emissions, after 2100 such temperatures could occur as often as every 3.5 years. Vautard, R. et al. [2] assess that the estimated recurrence intervals of heat waves such as July 2019 in the UK and Germany are currently around 10–30 years, but this probability under global climate change could increase by as much as 10-fold, which would mean they occur every 1 to 3 years. Extremely hot summers like 2003 and 2018 are projected to become the norm by 2050 which, under current climate projections, could lead to a 257% increase in heat-related mortality by 2050, the majority of which will be vulnerable people such as the elderly [4].

1.2. Present and Future of Indoor Temperatures in Residential Buildings in a Temperate Climate

The immediate trigger for a new approach to building overheating in temperate European countries was the August 2003 heat wave in Western Europe, which led to the highest number of heat-related deaths in history. Most studies on the future risk of a recurrence have been undertaken in the UK. These have shown that many buildings in temperate European countries are already exceeding recommended summer temperatures and that this effect will increase significantly over the next decades [5,6,7,8,9]. Buildings with low energy consumption are usually considered particularly vulnerable to overheating during summer heat waves, although this is not due to increasing the thermal insulation of the envelope [10], but rather to its high air-tightness [11,12,13] and low thermal inertia [14,15,16,17,18,19]. The concepts of passive houses [20] and zero-energy houses are becoming increasingly popular [19]. However, many studies indicate that these building solutions will be the most vulnerable to overheating [7,12,21,22], especially since simulation studies for future weather scenarios indicate that building temperatures will increasingly rise over the next few decades, even with the most drastic measures to reduce greenhouse gas emissions.

1.3. Passive Measures to Prevent Overheating in Residential Buildings

The most common way to counteract the effects of severe heat waves in residential buildings in relatively wealthy countries with temperate climates, e.g., the EU is to install, at least in selected rooms, individual air-conditioning units to eliminate the most intense discomfort experienced at that time. Some studies indicate that residential air conditioner saturation in temperate European countries will be dominated by homeowners’ subjective decisions made during periods of severe thermal discomfort during long and severe heat waves, which will become an integral part of the climate in just a few decades [23,24,25,26].
An alternative method, increasingly recommended by experts in many countries, to reduce the risk of overheating in dwellings during heat waves in temperate climates is the use of so-called passive methods to reduce temperature extremes. It can be achieved by an appropriate combination of window size and orientation [11,27,28], sun protection by shading [29,30,31,32], night ventilation [12,27,33,34], and high exposed thermal mass [16,18,35,36,37]. The first two measures are aimed at preventing heat from solar radiation from entering the building. High thermal capacity and night ventilation serve to distribute the process of heat transfer over time through the internal surfaces of the building envelope and to remove it to the outside. Many studies combine efficiency of increasing building thermal capacity with its coupling with additional night ventilation [38,39,40].

1.4. Passive Measures and User Expectations and Behavior

The decision of what the structure of buildings will be, light or heavy, is taken in the design phase. The occupant does not have the option to change it during the lifetime of the building, and thus has no possibility to affect the resulting thermal comfort of the rooms. In contrast, the situation is very different with the other two main passive methods of preventing overheating in summer: night ventilation and window shading. In residential buildings, night ventilation is generally provided by opening windows, which is highly dependent on occupant behavior [41]. Similarly, the shading of windows through the use of external and internal blinds depends on the users’ preferences [42]. Factors affecting occupant can be assigned to five broader categories [33,41]:
  • Physical environmental: weather, air quality, air temperature and humidity, noise, odors,
  • contextual: building archetype, construction, location, window orientation, neighborhood, A/C and ventilation systems and their control, etc.,
  • physiological: age, gender, health status, activity level, past thermal experience, clothing, food energy value,
  • psychological: attitudes, preferences, values, habits, concerns, expectations concerning thermal comfort, visual comfort, acoustical comfort, health, safety, financial and environmental concerns), cognitive resources (the level of awareness regarding environmental aspects, lifestyle, etc.),
  • social: sociocultural norms and practices or cultural background referring to the interaction between occupants, the structure of the decision-making hierarchy related to the control of the internal environment (e.g., the thermostat set point, the opening/closing of windows or blinds).
The last two categories are closely connected to the social science both sociology and psychology. Schweiker [43] calls them “internal or individual factors”. Of particular importance in the analysis of behaviors for the residents’ provision of acceptable microclimate conditions in dwellings appear to be psychological determinants in the area of behavioral psychology [44,45,46]. An overall regression analysis showed that six factors: comfort, health, individual’s role, belief in science, legitimacy of the energy crisis, and effort to conserve, significantly explained nearly 60% of the summer consumption variance and the comfort factor alone was the best predictor of summer electric consumption, primarily air conditioning [47].
Studies have shown that differences in occupant behavior can lead to two-, three-, and even six-fold higher energy use in identical dwellings [33]. In a study of 500 children bedrooms in Denmark Beko et al. [48] showed that occupant behavior is a much stronger predictor of air exchange than building characteristics. They also found significantly lower air exchange rates in bedrooms on the first floor of residential buildings compared to upper floors. The authors suggest that these results may reflect different ventilation habits of the occupants during the night. According to Lomas and Porritt [49] rooms in new low-energy dwellings tend to be of a lower height and are often single aspect, which prevents cross-ventilation. For aesthetic reasons, large windows are increasingly installed, which are often heavy and difficult to open. Additional factors limiting the practical application of natural ventilation in apartments are noise from city traffic, air pollution and safety concerns especially on the first floor. All these factors cause significant limitations in the practical possibility of using night ventilation during the summer heat, especially among the elderly. “More than half of respondents ... were unable to open windows when needed for security reasons’ and ‘even on a very hot day more than one in five respondents ... would not tend to open any windows at night’ and ‘one-third ... would not open windows due to high external noise levels” [49]. The same authors point to the much more frequent use of window shading, which according to occupant survey can be as high as 75% during hot weather. Conversely, Zuurbier [50] in a study conducted during the heatwave of 14–20 August 2012 in 113 dwellings in the Netherlands that were representative of the elderly found no significant effect of outdoor temperature neither on the windows opening to increase air exchange, nor on their shading to protect them from excessive sunlight.

1.5. Thermal Mass

While the effectiveness of night ventilation or window shading is directly related to the values, expectations and consequently the behavior of the occupants, the thermal capacity of a building is a parameter that is completely independent of occupant behavior. Methods based on the use of traditional building materials with high thermal capacity and PCMs, which absorb heat during the melting phase, are proposed. The use of traditional building materials with high thermal capacity is often criticized because of the high embodied energy attributed to them [51,52,53,54]. On the other hand, high embodied energy is also attributed to passive PCM applications in buildings [55,56,57]. More importantly, the efficiency of PCM materials is most often affected by the difficulty of matching the optimal melting temperature of the PCM used with the actual indoor air temperature which can be highly variable during the summer [58,59,60,61]. In newly designed buildings, traditional materials with high thermal mass can be effectively used, although some studies, while not questioning their effectiveness in hot climates, contest their usefulness in moderate and cold climates [62]. Residential buildings in Poland are usually constructed using traditional methods with masonry walls. Massive ceilings and floors also prevail over lightweight constructions. Despite the noticeable increase in popularity of lightweight wooden structures in recent years, their share in the Polish residential construction market is negligible and does not exceed 2% of newly erected buildings [63].
It was hypothesized that using a single passive method of increasing the thermal mass of walls and ceilings by using traditional building materials to cover their interior surfaces would significantly reduce the risk of overheating in living-rooms during intense heat waves in a temperate climate.
The main objective of this study was to show that in European countries with a temperate climate, the preservation of residential construction methods with heavyweight envelopes and partitions can significantly reduce the risk of overheating in residential living rooms over the next few decades, without the need for night ventilation or external blinds, the effectiveness of which is highly dependent on individual occupant behavior. This should lead to substantial reduction of the number of newly installed air conditioners in residential buildings. Due to the lower maximum temperature thresholds used in bedrooms, it may be necessary to additionally equip them with external blinds, which may be easier to operate than in living rooms because of their night-time use.

2. Methodology

2.1. Characteristics of Experimental Rooms

Experimental rooms are located at the south facade of the Center for Sustainable Building and Energy (CSBE) in The Science and Technology Park in Nowy Kisielin, in central-western Poland (Figure 1 and Figure 2). Nowy Kisielin is a small district in the city of Zielona Góra (Cfb-climate), located 8 k m from its center. CSBE is a three-storey, low energy center for research, science and development, that was put into use at the end of 2013. The usable area of the building is approximately 2500 m2.
Each experimental room is 6 m long, 3 m wide and 3.2 m high. The floor area of the rooms is 18 m2 and the net volume is about 57 m 3 . The internal surfaces of the roofs and walls of the rooms are made of different building materials. A window to floor area ratio is 0.25 .

2.2. Materials and Constructions

The analysis includes 4 types of construction of walls and roof assemblies located in experimental rooms H, VH, MH, L:
  • Type 1: light residential buildings, rather uncommon in Poland, but growing in popularity in recent years (with walls and ceiling based on a timber frame filled with mineral wool and with plasterboard on the inside—Room L; thermal mass parameter = 152 k J /( m 2 K )
  • Type 2: medium heavy construction (concrete floor with gres tiles, walls—lime sand blocks with gypsum plaster ceiling based on a timber frame filled with mineral wool and with plasterboard on the inside)—Room MH; thermal mass parameter = 474 k J /( m 2 K )
  • Type 3: heavy construction, very common in Polish residential buildings (concrete floor with gres tiles, walls—lime sand blocks with gypsum plaster, reinforced concrete roof with gypsum plaster,)—Room H; thermal mass parameter = 724 k J /( m 2 K )
  • Type 4: very heavy construction, rather uncommon in the residential buildings in Poland which ensure the greatest possible effective thermal mass (concrete floor with gres tiles, reinforced concrete walls and ceiling with no plaster, resulting in a strongly exposed concrete surface)—Room VH; thermal mass parameter = 922 k J /( m 2 K )
In Figure 3, a photo of example Room L was presented.
In Table 1 and Table 2, thermal transmittance coefficients and area of assemblies of experimental rooms as well as thermo-physics properties of materials were presented, respectively.

2.3. Measurements

The following measurements were recorded continuously:
  • inside the experimental rooms (air temperature and air humidity),
  • outside the building (outdoor parameters: air temperature and global horizontal solar radiation).
Indoor air temperatures in experimental rooms were measured by thermo-hygrometers (LUMEL, Type P18; uncertainty ± 0.5 %). The recorders were calibrated one month before the test period by the producer, who determined their accuracy to be ± 0.3 K . Immediately before the start of the study, preliminary measurements were carried out, to select them so that the differences in their readings under the same measuring conditions at room temperature would not exceed 0.1 K . They were located at a height of 1.2 m in the corner of experimental room 50 c m from the walls (Figure 2). The thermo-hygrometers also measured relative humidity; with an accuracy of ± 3 % declared by the producer. The preliminary measurements showed that the differences in their readings under the same measuring conditions at room temperature did not exceed 2.0 %. Outdoor temperature was measured by thermo-hygrometer (Delta OHM, Type HD9008TRR; uncertainty ± 0.1 %) placed in a Multiplate radiation shield Delta OHM, Type HD9007A1), whereas solar radiation was measure by pyranometer (Delta OHM, Type LP PYRA 03; sensitivity 10 μ V / m 2 ). These instruments were located at a local meteorological station next to the CSBE building. Regular measurements of all above mentioned parameters have been carried out since the end of December, 2013 and recorded in the BMS (Building Management System) every 5 min. The study was conducted during 3 heat waves in summer 2019:
(a)
1–30 June (mean outdoor temperature 22.7 °C; mean maximum outdoor temperature 30.1 °C),
(b)
23–30 July (mean outdoor temperature 24.0 °C; mean maximum outdoor temperature 29.9 °C),
(c)
24 August to 1 September (mean outdoor temperature 23.5 °C; mean maximum outdoor temperature 31.1 °C).
During the first two heat waves, the effectiveness of using light, medium-heavy and extra-heavy construction was compared. During the third heat wave, the effectiveness of heavy construction was additionally tested. All tests were conducted with the exterior blinds open and a constant ventilation air exchange of 0.6 ACH.
The data obtained in the study were checked for distribution and homogeneity of variance. The Shapiro–Wilk test showed that the temperature data distribution is similar to a normal distribution in all four room types. The Levene’s test confirmed the homogeneity of variance in all tested groups. The results of both tests allow the comparison of the obtained data by parametric tests. Therefore, (in order to compare the temperatures in the four rooms studied) a one-way ANOVA analysis of variance was performed. Appropriate post hoc tests were also performed to refine the analyses. For comparison of three rooms (L, M, VH), Bonferroni test was used, and for multiple comparisons of four buildings (due to unequal number of measurements in groups), Hochberg test was performed. The results of the Bonferroni test showed significant temperature differences between all three groups ( p < 0.001 ). Hochberg’s test showed that gr. M and H are not significantly different from each other, while all other groups show statistically significant differences in temperature ( p < 0.05 ).

3. Results and Discussion

Figure 4, Figure 5 and Figure 6 show the hourly air temperature courses in rooms L, M, and VH for the three heat waves of June, July, and August 2019, and additionally the hourly temperature course in room H for the August heat wave. June 2019, with an average temperature of 22.7 °C, turned out to be the warmest in the entire history of meteorological measurements. The course of temperatures in June 2019, however, was not typical of a heat wave, as the temperature increased and decreased several times throughout its duration. During a typical heat wave, which generally lasts much shorter, the temperature builds up in the first few days and remains high for the next few days. This is how the outside temperature evolved during the periods of the 8-day heat wave from 23 to 30 July with an average temperature of 24.0 °C and from 24 August to 1 September with an average temperature of 23.9 °C.
Increasing the thermal mass of the room from light to medium-heavy reduced the average maximum daytime temperature by 2.2 K during the first heat wave and by 2.6 K during the two other heat waves. The use of the very heavy structure further reduced the average peak temperature for the subsequent heat waves by 1.4 K , 1.2 K and 1.7 K . A six-fold increase in the thermal mass of the very light 152 k J /( m 2 K ) structure to the very heavy 922 k J /( m 2 K ) structure led to a reduction in peak daytime temperatures during the subsequent heat waves by 3.6 K , 3.8 K , and 4.3 K , respectively. Much more realistic than the use of reinforced concrete wall and floor surfaces in the conditions of typical construction technologies used in Poland seems to be plastering of the roof with a layer of gypsum plaster and replacement of reinforced concrete walls with plastered masonry walls. This type of construction currently accounts for more than 98% of all new buildings constructed in Poland. During the 9 day heat wave from 24 August to 1 September, indoor temperatures were compared between the heavy room and the very heavy room. The maximum daytime temperature in the heavy room was on average 0.8 K higher than in the very heavy room. There is increasing pressure to increase the market share of lightweight construction, mainly based on light timber frame structures. On the basis of the study, it can be expected that if such lightweight solutions are applied to the walls and ceilings of buildings, the maximum temperatures during the period of intense heat waves would increase significantly.
An interesting finding was reached by observing the effect of increasing thermal mass on the course of internal temperatures at night. The increase in thermal mass from light to very heavy led to a decrease in minimum night time temperatures averaging about 0.8 K during the 3 heat waves. In the absence of night ventilation, the temperature in the high thermal mass rooms decreased significantly slower than in the light ones, but did not worsen the thermal comfort of the rooms.
As can be seen, the obtained effects of reduced indoor temperature due to increased thermal mass are consistent with other experimental results conducted in the last two decades in a temperate and cold climate (Table 3).
In order to assess the influence of thermal mass of rooms on the thermal comfort of users, national standards, e.g., CIBSE TM52, or ASHRAE Standard 55-2017, or international standards, e.g., EN 16798-1, are used. In this paper, the methodology given in CIBSE TM52 criteria 1 and 3 was used for this purpose, which, respectively, allow us to estimate the scale of thermal comfort exceedances and temperature exceedances at extremely high temperatures. For criterion 3, 2 adaptive temperature thresholds were used for this purpose T m a x + 3 , recommended for new or renovated buildings, and T m a x + 4 , suggested for existing buildings. This methodology for assessing thermal comfort was used because, as already mentioned, in residential buildings, the overheating during the most severe heat waves is the main determinant of the installation of air conditioning equipment.
The analysis of hours of exceedance according to CIBSE TM52 criterion 1 does not allow for a full assessment of the benefits of the increasing of thermal mass. For the June and July heat waves, the amounts of hours exceeded for rooms with light and medium-heavy construction were only slightly different. A somewhat larger effect, a reduction of 22.6 % for the June heat wave and 36.8 % for the July heat wave, was obtained using the very heavy construction. For the August heat wave, increasing the thermal mass had no effect on the number of exceeding hours, regardless of the magnitude of its increase.
For a more comprehensive comparison of the effect of thermal mass on the exceedance hours, an analysis in which their number is related to the absolute maximum temperature Tupp (CIBSE TM 52).
In Figure 7, Figure 8 and Figure 9, the hourly course of temperature in the studied rooms is compared with the maximum temperature and the absolute maximum temperature calculated for category II—new buildings and renovations, and for category III—existing buildings according to CIBSE TM–52.
With the threshold temperature for category II, the reduction of hours exceeding the allowed temperature for the three consecutive heat waves in summer 2019 were 75.5%, 100%, and 49.0%, respectively. With the threshold temperature for category III, the reduction of hours exceeding the allowed temperature for the three consecutive heat waves in summer 2019 were, 75.5%, 100%, and 49.0%.
Using the threshold temperature for CIBSE category II, increasing the thermal mass from light to medium led to a reduction in the number of exceedance hours by 29.4% during the June heat wave, by 75.9% during the July heat wave, and by 6.8% during the August heat wave, respectively. With the CIBSE Category III temperature limit, the number of exceedance hours was reduced by 59.5% during the June heat wave and by 36.0% for the August heat wave. During the July heat wave, the hours of exceedance were completely eliminated in this case.
Increasing the thermal mass from light to very heavy led to a reduction of the hours exceeding the threshold temperature for category II by 76.6% in June and by 13.6% in August. For the threshold temperature for category III, the corresponding reduction in exceedance hours was 96.7% for the June heat wave and 76.0% for the August heat wave. As with the medium thermal mass construction for the very heavy thermal mass structure, the exceedance hours were completely eliminated for the July heat wave.
The study showed that while the use of increasing a building’s thermal mass as the only passive method of counteracting high temperatures during heat waves does not lead to significant improvements in thermal comfort, it is able to significantly reduce the frequency of temperatures considered to be the maximum allowable for occupants and, as a result, reduce the risk of them deciding to install air conditioning equipment.
The analysis of hours of exceedances for three heat waves presented in Figure 7, Figure 8 and Figure 9 on the background of graphs of internal and external temperature courses presented in Figure 4, Figure 5 and Figure 6 shows that daily characteristics of external temperature, its maximum, average and minimum values, do not fully determine the scale of possible overheating of buildings. Other important factors include the duration of the heat wave, the way in which outdoor temperatures are distributed during its successive days, as well as the value of indoor temperatures in individual rooms in the period immediately preceding the heat wave. The period most vulnerable to the occurrence of extremely high indoor temperatures turned out to be the August heat wave, during which the maximum daytime temperature was above 30 °C on the last 7 days and above 32 °C on the last 5 days. For example, during the July heat wave, although the average daily temperature remained similar to August’s 24 °C v. 23.9 °C, the splitting of days with very high temperatures with days with lower temperatures led to significantly lower indoor temperatures for all investigated rooms.
In order to better illustrate the effect of increasing the thermal mass of walls and roof on the thermal comfort of the residents during typical heat waves in Figure 10 daily temperature courses in individual rooms were plotted in relation to T m a x , T m a x + 3 and T m a x + 4 for the July heat wave.
In the light room, the temperature T m a x + 4 was exceeded regularly except on the first day of this period. The same temperature was not exceeded in one day in either the very heavy room or the medium-heavy room. T m a x + 4 was exceeded in the light room on the same number of days as T m a x + 3 . In the very heavy room, it was not exceeded even once, and in the medium-heavy room it was exceeded on the last 3 days of the heat wave.

4. Conclusions

The main objective of this paper was to demonstrate the effectiveness of increasing the thermal mass of the rooms in real building by using traditional building materials to reduce the risk of its excessive overheating during intense heat waves in a temperate climate. An additional objective was to show that the use of this single passive measure significantly reduces the risk of overheating in daytime rooms, but also, though to a much lesser extent, in bedrooms.
The discussion in this paper of the effect of occupant behavior on the effective use of night ventilation through windows and protection from the sun by closing blinds during hot and sunny weather showed that occupants do not make proper use of both passive methods. This is particularly evident in buildings for the elderly.
Increasing the thermal mass of the room from light to a medium-heavy reduced the average maximum daily temperature by 2.2 K during the first heat wave and by 2.6 K during the two other heat waves. The use of very heavy construction further reduced the average maximum temperature for the heat waves analyzed by 1.4 K , 1.2 K and 1.7 K , respectively, giving a total possible reduction in maximum daily temperatures in the range of 3.6 °C, 3.8 °C and 4.3 °C.
The analysis of obtained results indicates that daily characteristics of external temperature, its maximum, average and minimum values, do not fully determine the scale of possible overheating of buildings. Other important factors include the duration of the heat wave, the way in which outdoor temperatures are distributed during its successive days, as well as the value of indoor temperatures in individual rooms in the period immediately preceding the heat wave
The study showed that while the use of increasing a building’s thermal mass as the only passive method of counteracting high temperatures during heat waves did not lead to significant improvements in thermal comfort, it was able to significantly reduce the frequency of temperatures considered to be the absolute maximum allowable for occupants and, as a result, reduce the risk that they will choose to install air conditioning units. The results suggest that the use of heavyweight residential buildings in European temperate countries may significantly reduce the installation of air-conditioning equipment in daytime rooms for over the next 20–30 years, without the need for night ventilation or external blinds, which are highly dependent on individual occupant behavior.
The considerations presented in this paper apply to daytime rooms only. The effect of increasing thermal mass at night was significant, but much smaller than at peak daytime temperatures. Because of this and the lower temperature thresholds in bedrooms, future research should include the combined effect of thermal mass and external blinds. In bedrooms used at night, closing blinds during the day may be much more socially acceptable than in living rooms.

Work Limitations and Future Work

When analyzing the results of the study, it should be remembered that the rooms studied were located on the top floor and were equipped with large south-facing windows. For rooms located on lower floors or in a different orientation with respect to the directions of the world, it can be expected that the thermal load from solar radiation will be significantly lower, which should result in a reduction of internal temperatures.
On the other hand, the research was conducted in an unused room. The decision to conduct research in such conditions was made taking into account both literature data on uncontrolled but very significant influence of users’ behavior on the evolution of internal temperature in the room and authors’ own experimental experience in this field. Future research should focus on finding out to what extent, by changing these parameters, the operating temperatures of these rooms can be reduced during heat waves. A full analysis of the effectiveness of increasing the thermal mass, allowing us to establish quantitative relations between the thermal mass of the rooms and the degree of reduction of their maximum temperature, taking into account the heat gains from the occupants and the expected external loads from solar radiation for other room locations and window areas, will be possible only by modeling, which was assumed as a continuation of the present work.

Author Contributions

Conceptualization, T.K.; methodology, A.S.; formal analysis, P.Z.; investigation, T.K. and A.S.; resources, T.K., A.S. and A.P.; data curation, A.P.; writing—original draft preparation, T.K., A.S., A.P.; writing—review and editing, P.Z.; visualization, P.Z. and A.S.; supervision, T.K. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Informed Consent Statement

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

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Christidis, N.; McCarthy, M.; Stott, P.A. The increasing likelihood of temperatures above 30 to 40 °C in the United Kingdom. Nat. Commun. 2020, 11, 1–10. [Google Scholar] [CrossRef]
  2. Jan van Oldenborgh, G.; Philip, S.; Kew, S.; Otto, F.; Haustein, K.; Vautard, R.; Boucher Jean-Michel Soubeyroux, O.; Ribes, A.; Robin Sonia Seneviratne, Y.I.; Vogel, M.M. Human Contribution to the Record-Breaking June 2019 Heat Wave in France; Technical Report; World Weather Attribution: Paris, France, 2019. [Google Scholar]
  3. McCarthy, M.; Christidis, N.; Dunstone, N.; Fereday, D.; Kay, G.; Klein-Tank, A.; Lowe, J.; Petch, J.; Scaife, A.; Stott, P. Drivers of the UK summer heatwave of 2018. Weather 2019, 74, 390–396. [Google Scholar] [CrossRef]
  4. Hughes, C.; Natarajan, S. Summer thermal comfort and overheating in the elderly. Build. Serv. Eng. Res. Technol. 2019, 40, 426–445. [Google Scholar] [CrossRef]
  5. Beizaee, A.; Lomas, K.J.; Firth, S.K. National survey of summertime temperatures and overheating risk in English homes. Build. Environ. 2013, 65, 1–17. [Google Scholar] [CrossRef] [Green Version]
  6. Wright, A.; Young, A.; Natarajan, S. Dwelling temperatures and comfort during the August 2003 heat wave. Build. Serv. Eng. Res. Technol. 2005, 26, 285–300. [Google Scholar] [CrossRef]
  7. Tabatabaei Sameni, S.M.; Gaterell, M.; Montazami, A.; Ahmed, A. Overheating investigation in UK social housing flats built to the Passivhaus standard. Build. Environ. 2015, 92, 222–235. [Google Scholar] [CrossRef] [Green Version]
  8. Hamdy, M.; Carlucci, S.; Hoes, P.J.; Hensen, J.L. The impact of climate change on the overheating risk in dwellings—A Dutch case study. Build. Environ. 2017, 122, 307–323. [Google Scholar] [CrossRef]
  9. Pathan, A.; Mavrogianni, A.; Summerfield, A.; Oreszczyn, T.; Davies, M. Monitoring summer indoor overheating in the London housing stock. Energy Build. 2017, 141, 361–378. [Google Scholar] [CrossRef]
  10. Taylor, J.; Mavrogianni, A.; Davies, M.; Das, P.; Shrubsole, C.; Biddulph, P.; Oikonomou, E. Understanding and mitigating overheating and indoor PM 2.5 risks using coupled temperature and indoor air quality models. Build. Serv. Eng. Res. Technol. 2015, 36, 275–289. [Google Scholar] [CrossRef]
  11. Tian, Z.; Zhang, S.; Deng, J.; Dorota Hrynyszyn, B. Evaluation on Overheating Risk of a Typical Norwegian Residential Building under Future Extreme Weather Conditions. Energies 2020, 13, 658. [Google Scholar] [CrossRef] [Green Version]
  12. Psomas, T.; Heiselberg, P.; Duer, K.; Bjørn, E. Overheating risk barriers to energy renovations of single family houses: Multicriteria analysis and assessment. Energy Build. 2016, 117, 138–148. [Google Scholar] [CrossRef]
  13. Abdulla, Z.; Rodrigues, L. The effect of shading, infiltration and ventilation levels on overheating and heating demands in UK residential buildings. Case study: Trent Basin Regeneration. In Proceedings of the 36th International Conference on Passive and Low Energy Architecture, Cities, Buildings, People: Towards Regenerative Environments (PLEA 2016), Los Angeles, CA, USA, 11–13 July 2016. [Google Scholar]
  14. Adekunle, T.O.; Nikolopoulou, M. Thermal comfort, summertime temperatures and overheating in prefabricated timber housing. Build. Environ. 2016, 103, 21–35. [Google Scholar] [CrossRef]
  15. Rodrigues, L.; Sougkakis, V.; Gillott, M. Investigating the potential of adding thermal mass to mitigate overheating in a super-insulated low-energy timber house. Int. J. Low-Carbon Technol. 2016, 11, 305–316. [Google Scholar] [CrossRef] [Green Version]
  16. Stazi, F.; Tomassoni, E.; Di Perna, C. Super-insulated wooden envelopes in Mediterranean climate: Summer overheating, thermal comfort optimization, environmental impact on an Italian case study. Energy Build. 2017, 138, 716–732. [Google Scholar] [CrossRef]
  17. Gamero-Salinas, J.C.; Monge-Barrio, A.; Sánchez-Ostiz, A. Overheating risk assessment of different dwellings during the hottest season of a warm tropical climate. Build. Environ. 2020, 171, 106664. [Google Scholar] [CrossRef]
  18. Pomfret, L.; Hashemi, A. Thermal Comfort in Zero Energy Buildings. Energy Procedia 2017, 134, 825–834. [Google Scholar] [CrossRef] [Green Version]
  19. Kurnitski, J.; Saari, A.; Kalamees, T.; Vuolle, M.; Niemelä, J.; Tark, T. Cost optimal and nearly zero (nZEB) energy performance calculations for residential buildings with REHVA definition for nZEB national implementation. Energy Build. 2011, 43, 3279–3288. [Google Scholar] [CrossRef]
  20. Niskanen, J.; Rohracher, H. Passive houses as affiliative objects: Investment calculations, energy modelling, and collaboration strategies of Swedish housing companies. Energy Res. Soc. Sci. 2020, 70, 101643. [Google Scholar] [CrossRef]
  21. Jones, R.V.; Goodhew, S.; De Wilde, P. Measured indoor temperatures, thermal comfort and overheating risk: Post-occupancy evaluation of low energy houses in the UK. Energy Procedia 2016, 88, 714–720. [Google Scholar] [CrossRef] [Green Version]
  22. Dartevelle, O.; van Moeseke, G.; Mlecnik, E.; Altomonte, S. Long-term evaluation of residential summer thermal comfort: Measured vs. perceived thermal conditions in nZEB houses in Wallonia. Build. Environ. 2021, 190, 107531. [Google Scholar] [CrossRef]
  23. Puckett, K.; Gethering, W. Design for Climate Change; Riba Publishing: London, UK, 2013; p. 196. [Google Scholar]
  24. Peacock, A.D.; Jenkins, D.P.; Kane, D. Investigating the potential of overheating in UK dwellings as a consequence of extant climate change. Energy Policy 2010, 38, 3277–3288. [Google Scholar] [CrossRef]
  25. Jakubcionis, M.; Carlsson, J. Estimation of European Union residential sector space cooling potential. Energy Policy 2017, 101, 225–235. [Google Scholar] [CrossRef]
  26. Andreou, A.; Barrett, J.; Taylor, P.G.; Brockway, P.E.; Wadud, Z. Decomposing the drivers of residential space cooling energy consumption in EU-28 countries using a panel data approach. Energy Built Environ. 2020, 1, 432–442. [Google Scholar] [CrossRef]
  27. Birchmore, R.; Davies, K.; Etherington, P.; Tait, R.; Pivac, A. Overheating in Auckland homes: Testing and interventions in full-scale and simulated houses. Build. Res. Inf. 2017, 45, 157–175. [Google Scholar] [CrossRef]
  28. Amaral, A.R.; Rodrigues, E.; Gaspar, A.R.; Gomes, Á. A thermal performance parametric study of window type, orientation, size and shadowing effect. Sustain. Cities Soc. 2016, 26, 456–465. [Google Scholar] [CrossRef] [Green Version]
  29. Rodrigues, L.T.; Gillott, M.; Tetlow, D. Summer overheating potential in a low-energy steel frame house in future climate scenarios. Sustain. Cities Soc. 2013, 7, 1–15. [Google Scholar] [CrossRef]
  30. Zukowska, D.; Ananida, M.; Kolarik, J.; Sarey Khanie, M.; Rammer Nielsen, T. Solar control solutions for reducing overheating risks in retrofitted Danish apartment buildings from the period 1850–1900—A simulation-based study. E3S Web Conf. 2019, 111. [Google Scholar] [CrossRef] [Green Version]
  31. Grussa, Z.D.; Andrews, D.; Lowry, G.; Newton, E.J.; Yiakoumetti, K.; Chalk, A.; Bush, D. A London residential retrofit case study: Evaluating passive mitigation methods of reducing risk to overheating through the use of solar shading combined with night-time ventilation. Build. Serv. Eng. Res. Technol. 2019, 40, 389–408. [Google Scholar] [CrossRef]
  32. Ibrahim, A.; Pelsmakers, S.L. Low-energy housing retrofit in North England: Overheating risks and possible mitigation strategies. Build. Serv. Eng. Res. Technol. 2018, 39, 161–172. [Google Scholar] [CrossRef] [Green Version]
  33. Mavrogianni, A.; Davies, M.; Taylor, J.; Chalabi, Z.; Biddulph, P.; Oikonomou, E.; Das, P.; Jones, B. The impact of occupancy patterns, occupant-controlled ventilation and shading on indoor overheating risk in domestic environments. Build. Environ. 2014, 78, 183–198. [Google Scholar] [CrossRef]
  34. Lee, W.V.; Shaman, J. Heat-coping strategies and bedroom thermal satisfaction in New York City. Sci. Total. Environ. 2017, 574, 1217–1231. [Google Scholar] [CrossRef] [Green Version]
  35. Kalema, T.; Jóhannesson, G.; Pylsy, P.; Hagengran, P. Accuracy of Energy Analysis of Buildings: A Comparison of a Monthly Energy Balance Method and Simulation Methods in Calculating the Energy Consumption and the Effect of Thermal Mass. J. Build. Phys. 2008, 32, 101–130. [Google Scholar] [CrossRef]
  36. Brambilla, A.; Jusselme, T. Preventing overheating in offices through thermal inertial properties of compressed earth bricks: A study on a real scale prototype. Energy Build. 2017, 156, 281–292. [Google Scholar] [CrossRef]
  37. Kuczyński, T.; Staszczuk, A. Experimental study of the influence of thermal mass on thermal comfort and cooling energy demand in residential buildings. Energy 2020, 195, 116984. [Google Scholar] [CrossRef]
  38. Gagliano, A.; Nocera, F.; Patania, F.; Moschella, A.; Detommaso, M.; Evola, G. Synergic effects of thermal mass and natural ventilation on the thermal behaviour of traditional massive buildings. Int. J. Sustain. Energy 2016, 35, 411–428. [Google Scholar] [CrossRef]
  39. Roucoult, J.M.; Douzane, O.; Langlet, T. Incorporation of thermal inertia in the aim of installing a natural nighttime ventilation system in buildings. Energy Build. 1999, 29, 129–133. [Google Scholar] [CrossRef]
  40. Brambilla, A.; Bonvin, J.; Flourentzou, F.; Jusselme, T. On the Influence of Thermal Mass and Natural Ventilation on Overheating Risk in Offices. Buildings 2018, 8, 47. [Google Scholar] [CrossRef] [Green Version]
  41. Fabi, V.; Andersen, R.V.; Corgnati, S.; Olesen, B.W. Occupants’ window opening behaviour: A literature review of factors influencing occupant behaviour and models. Build. Environ. 2012, 58, 188–198. [Google Scholar] [CrossRef]
  42. Van Den Wymelenberg, K. Patterns of occupant interaction with window blinds: A literature review. Energy Build. 2012, 51, 165–176. [Google Scholar] [CrossRef]
  43. Schweiker, M. Occupant Behaviour and the Related Reference Levels for Heating and Cooling. Ph.D. Thesis, Tokyo City University, Tokyo, Japan, 2010. [Google Scholar]
  44. Ajzen, I.; Brown, T.C.; Carvajal, F. Explaining the discrepancy between intentions and actions: The case of hypothetical bias in contingent valuation. Personal. Soc. Psychol. Bull. 2004, 30, 1108–1121. [Google Scholar] [CrossRef] [PubMed]
  45. Ajzen, I.; Fishbein, M. The influence of attitudes on behaviour. In The Handbook of Attitudes; Albarracìn, D., Johnson, B., Zanna, M., Eds.; Erlbaum: Washington, DC, USA, 2005; pp. 173–221. [Google Scholar]
  46. Refsgaard, K.; Magnussen, K. Household behaviour and attitudes with respect to recycling food waste–experiences from focus groups. J. Environ. Manag. 2009, 90, 760–771. [Google Scholar] [CrossRef] [PubMed]
  47. Seligman, C.; Kriss, M.; Darley, J.M.; Fazio, R.H.; Becker, L.J.; Pryor, J.B. Predicting Summer Energy Consumption from Homeowners’ Attitudes1. J. Appl. Soc. Psychol. 1979, 9, 70–90. [Google Scholar] [CrossRef]
  48. Bekö, G.; Toftum, J.; Clausen, G. Modeling ventilation rates in bedrooms based on building characteristics and occupant behavior. Build. Environ. 2011, 46, 2230–2237. [Google Scholar] [CrossRef]
  49. Lomas, K.J.; Porritt, S.M. Overheating in buildings: Lessons from research. Build. Res. Inf. 2017, 45, 1–18. [Google Scholar] [CrossRef] [Green Version]
  50. Zuurbier, M.; van Loenhout, J.A.F.; le Grand, A.; Greven, F.; Duijm, F.; Hoek, G. Street temperature and building characteristics as determinants of indoor heat exposure. Sci. Total. Environ. 2021, 766, 144376. [Google Scholar] [CrossRef]
  51. Börjesson, P.; Gustavsson, L. Greenhouse gas balances in building construction: Wood versus concrete from life-cycle and forest land-use perspectives. Energy Policy 2000, 28, 575–588. [Google Scholar] [CrossRef]
  52. Gustavsson, L.; Pingoud, K.; Sathre, R. Carbon dioxide balance of wood substitution: Comparing concrete- and wood-framed buildings. Mitig. Adapt. Strateg. Glob. Chang. 2006, 11, 667–691. [Google Scholar] [CrossRef]
  53. Lenzen, M.; Treloar, G. Embodied energy in buildings: Wood versus concrete—Reply to Börjesson and Gustavsson. Energy Policy 2002, 30, 249–255. [Google Scholar] [CrossRef]
  54. Gerilla, G.P.; Teknomo, K.; Hokao, K. An environmental assessment of wood and steel reinforced concrete housing construction. Build. Environ. 2007, 42, 2778–2784. [Google Scholar] [CrossRef]
  55. De Gracia, A.; Rincón, L.; Castell, A.; Jiménez, M.; Boer, D.; Medrano, M.; Cabeza, L.F. Life Cycle Assessment of the inclusion of phase change materials (PCM) in experimental buildings. Energy Build. 2010, 42, 1517–1523. [Google Scholar] [CrossRef]
  56. Menoufi, K.; Castell, A.; Navarro, L.; Pérez, G.; Boer, D.; Cabeza, L.F. Evaluation of the environmental impact of experimental cubicles using Life Cycle Assessment: A highlight on the manufacturing phase. Appl. Energy 2012, 92, 534–544. [Google Scholar] [CrossRef]
  57. Castell, A.; Menoufi, K.; de Gracia, A.; Rincón, L.; Boer, D.; Cabeza, L.F. Life Cycle Assessment of alveolar brick construction system incorporating phase change materials (PCMs). Appl. Energy 2013, 101, 600–608. [Google Scholar] [CrossRef]
  58. Sage-Lauck, J.S.; Sailor, D.J. Evaluation of phase change materials for improving thermal comfort in a super-insulated residential building. Energy Build. 2014, 79, 32–40. [Google Scholar] [CrossRef]
  59. Alam, M.; Zou, P.X.; Sanjayan, J.; Ramakrishnan, S. Energy saving performance assessment and lessons learned from the operation of an active phase change materials system in a multi-storey building in Melbourne. Appl. Energy 2019, 238, 1582–1595. [Google Scholar] [CrossRef]
  60. Sinka, M.; Bajare, D.; Jakovics, A.; Ratnieks, J.; Gendelis, S.; Tihana, J. Experimental testing of phase change materials in a warm-summer humid continental climate. Energy Build. 2019, 195, 205–215. [Google Scholar] [CrossRef]
  61. Khudhair, A.M.; Farid, M.M. Use of phase change materials for thermal comfort and electrical energy peak load shifting: Experimental investigations. In Proceedings of ISES World Congress 2007; Springer: Berlin/Heidelberg, Germany, 2007; Volume 1, pp. 283–288. [Google Scholar] [CrossRef]
  62. Reilly, A.; Kinnane, O. The impact of thermal mass on building energy consumption. Appl. Energy 2017, 198, 108–121. [Google Scholar] [CrossRef] [Green Version]
  63. GUS. Budownictwo w 2018 r.; Technical Report; GUS: Warszawa, Poland, 2019. [Google Scholar]
  64. Staszczuk, A.; Kuczyński, T. The impact of wall and roof material on the summer thermal performance of building in a temperate climate. Energy 2021, 228, 120482. [Google Scholar] [CrossRef]
  65. Bellamy, L.A.; Mackenzie, D.W. Thermal Performance of Buildings with Heavy Walls; BRANZ: Judgeford, New Zealand, 2002. [Google Scholar]
  66. Tink, V.; Porritt, S.; Allinson, D.; Loveday, D. Measuring and mitigating overheating risk in solid wall dwellings retrofitted with internal wall insulation. Build. Environ. 2018, 141, 247–261. [Google Scholar] [CrossRef]
  67. Jakovičs, A.; Gendelis, S.; Bandeniece, L. Energy efficiency and sustainability of different building structures in Latvian climate. In IOP Conference Series: Materials Science and Engineering; Institute of Physics Publishing: Riga, Latvia, 2015; Volume 96. [Google Scholar] [CrossRef]
  68. Grynning, S.; Nocente, A.; Gullbrekken, L.; Skjeggerud, K. Thermal mass and thermal comfort in offices—Experimental studies of a concrete floor. MATEC Web Conf. 2019, 282, 02087. [Google Scholar] [CrossRef]
  69. Vik, T.A.; Madessa, H.B.; Aslaksrud, P.; Folkedal, E.; Øvrevik, O.S. Thermal Performance of an Office Cubicle Integrated with a Bio-based PCM: Experimental Analyses. Energy Procedia 2017, 111, 609–618. [Google Scholar] [CrossRef]
  70. Ramakrishnan, S.; Wang, X.; Sanjayan, J.; Wilson, J. Thermal performance assessment of phase change material integrated cementitious composites in buildings: Experimental and numerical approach. Appl. Energy 2017, 207, 654–664. [Google Scholar] [CrossRef]
  71. Schossig, P.; Henning, H.M.; Gschwander, S.; Haussmann, T. Micro-encapsulated phase-change materials integrated into construction materials. Sol. Energy Mater. Sol. Cells 2005, 89, 297–306. [Google Scholar] [CrossRef]
  72. Voelker, C.; Kornadt, O.; Ostry, M. Temperature reduction due to the application of phase change materials. Energy Build. 2008, 40, 937–944. [Google Scholar] [CrossRef] [Green Version]
Figure 1. Center for Sustainable Building and Energy in The Science and Technology Park in Nowy Kisielin, Poland; view of the building facade and horizontal section.
Figure 1. Center for Sustainable Building and Energy in The Science and Technology Park in Nowy Kisielin, Poland; view of the building facade and horizontal section.
Energies 14 04117 g001
Figure 2. Plan of the top floor of the building with the locations of experimental rooms and thermo-hygrometers (indicated as red squares).
Figure 2. Plan of the top floor of the building with the locations of experimental rooms and thermo-hygrometers (indicated as red squares).
Energies 14 04117 g002
Figure 3. Room L (light construction); view of the room with location of ventilation and measurement system.
Figure 3. Room L (light construction); view of the room with location of ventilation and measurement system.
Energies 14 04117 g003
Figure 4. The temperature course in light, medium heavy, and very heavy rooms as a function of outdoor temperature and solar radiation during heat wave 1 through 30 June 2019.
Figure 4. The temperature course in light, medium heavy, and very heavy rooms as a function of outdoor temperature and solar radiation during heat wave 1 through 30 June 2019.
Energies 14 04117 g004
Figure 5. The temperature course in light, medium heavy, and very heavy rooms as a function of outdoor temperature and solar radiation during heat wave 23–30 July 2019.
Figure 5. The temperature course in light, medium heavy, and very heavy rooms as a function of outdoor temperature and solar radiation during heat wave 23–30 July 2019.
Energies 14 04117 g005
Figure 6. The temperature course in light, medium heavy, heavy and very heavy rooms as a function of outdoor temperature and solar radiation during heat wave 24 August–1 September 2019.
Figure 6. The temperature course in light, medium heavy, heavy and very heavy rooms as a function of outdoor temperature and solar radiation during heat wave 24 August–1 September 2019.
Energies 14 04117 g006
Figure 7. Hours of exceedance in all tested rooms during 1–30 June 2019, Hours 7:00–22:00.
Figure 7. Hours of exceedance in all tested rooms during 1–30 June 2019, Hours 7:00–22:00.
Energies 14 04117 g007
Figure 8. Hours of exceednce in all tested rooms during 23–30 July 2019, Hours 7:00–22:00.
Figure 8. Hours of exceednce in all tested rooms during 23–30 July 2019, Hours 7:00–22:00.
Energies 14 04117 g008
Figure 9. Hours of exceedance in all tested rooms during 24 August–1 September 2019, Hours 7:00–22:00.
Figure 9. Hours of exceedance in all tested rooms during 24 August–1 September 2019, Hours 7:00–22:00.
Energies 14 04117 g009
Figure 10. Daily temperature courses in individual rooms in relation to T m a x , T m a x + 3 and T m a x + 4 for the July heat wave.
Figure 10. Daily temperature courses in individual rooms in relation to T m a x , T m a x + 3 and T m a x + 4 for the July heat wave.
Energies 14 04117 g010
Table 1. Thermal transmittance coefficients and area of assemblies of experimental rooms.
Table 1. Thermal transmittance coefficients and area of assemblies of experimental rooms.
AssemblyU [W/(m2K)]A [m2]
External wall Room H 0.164 5
External wall Room VH 0.173 5
External wall Room MH 0.163 5
External wall Room L 0.116 5
Internal wall Seminar Room/H 0.462 19
Internal wall Room H/VH 0.506 19
Internal wall Room VH/MH 0.463 19
Internal wall surrounding room/L 0.205 19
Internal wall Room L/surrounding room 0.160 19
Internal wall Hall/Room H 0.420 8
Internal wall Hall/Room VH 0.456 8
Internal wall Hall/Room MH 0.431 8
Internal wall Hall/Room L 0.267 8
Floor Room H, VH, MH 0.584 18
Floor Room L 0.558 18
Roof Room H 0.115 18
Roof Room VH 0.116 18
Roof Room MH, L 0.083 18
Windows triple glazing, SHGC (av.) = 0.50 4.5
Uw-mounted = 0.79 W /( m 2 K ); Ug = 0.51 W /( m 2 K )
Table 2. Thermophysics properties of materials.
Table 2. Thermophysics properties of materials.
Material λ [W/(mK)] ρ [kg/m 3 ]c [J/(kg K)]
Air layer 0.28 1.3 1000
Aerated concrete blocks 0.105 400840
Ceramic brick 0.55 1900880
Concrete screed layer 1.15 18001000
EPS 0.044 201460
Floor carpeting 0.06 2001300
Gypsum board 0.25 9001000
Gypsum plaster 0.40 10001000
Gres tiles 1.10 2000920
Lime sand blocks 0.55 16001000
Mineral wool 0.036 901030
OSB 0.13 6501700
PE-Membrane 0.33 9202200
Bucket foil 0.50 9801800
Reinforced concrete 1.70 2500840
Roof covering (asphalt) 0.18 10001460
Textured plaster 0.82 1850840
Trapez metal sheet 1.70 2500840
Table 3. Effects of reduced indoor temperature due to increased thermal mass in other experimental results conducted in the last two decades in a temperate and cold climate.
Table 3. Effects of reduced indoor temperature due to increased thermal mass in other experimental results conducted in the last two decades in a temperate and cold climate.
AuthorsPlace of
Research
Type of
Climate
Type of
Research
Structural
Elements
ΔTmaxRef.
This researchZielona Góra,
Poland
(Cfb-climate)ExperimentalWalls &
roof
2.2–2.6 K
(M v. L)
3.6–4.3 K
(VH v. L)
2.8–3.5 K
(H v. L)
Kuczyński &
Staszczuk, 2020
Zielona Góra,
Poland
Cfb-climateExperimentalWalls1.5–2.5 K[37]
Staszczuk &
Kuczyński, 2021
Zielona Góra,
Poland
Cfb-climateExperimentalWalls &
roof *
1.5–2.5 K[64]
Bellamy &
Mckenzie, 2001
Lincoln,
New Zealand
Cfb-climateExperimentalWalls3.0–5.0 K[65]
Tink et al., 2018Leicestershire,
UK
Cfb-climateExperimentalWalls2.5 K[66]
Jakovics et al.,
2015
Riga,
Latvia
Cfb-climateExperimentalWalls3.0–4.0 K[67]
Grynning et al.,
2019
Trondheim,
Norway
Dfb-climateExperimentalFloor2.5–3.0 K[68]
Brambilla &
Jusselme, 2017
Fribourg,
Switzerland
Cfb-climateExperimentalWalls1.1–3.0 K[36]
Sage-Lauck &
Sailor, 2014
Portland,
USA
Cfb-climateExperimental
(PCM)
Walls &
roof
1.1 K[58]
Jamil et al., 2016Melbourne,
Australia
Cfb-climateExperimental
(PCM)
Roof1.1 K
Khudhair &
Farid, 2007
Auckland,
New Zealand
Cfb-climateExperimental
(PCM)
Walls &
roof
2.4 K[61]
Vik et al., 2017OsloDfb-climateExperimental
(PCM)
1 walls &
roof
3.3 K **
2.6 K ***
[69]
Ramaskrishnan
et al., 2017
Melbourne,
Australia
Cfb-climateExperimental
(PCM)
Walls &
roof
2.5–2.8 K[70]
Schossig et al.,
2016
Freiburg,
Germany
Cfb-climateExperimental
(PCM)
Walls &
roof
1.0–3.5 K[71]
Voelker et al.,
2007
Weimar,
Germany
Cfb-climateExperimental
(PCM)
Walls &
roof
0.5–4.0 K[72]
* External blinds closed. ** PCM; no gypsum board. *** PCM; gypsum board.
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Kuczyński, T.; Staszczuk, A.; Ziembicki, P.; Paluszak, A. The Effect of the Thermal Mass of the Building Envelope on Summer Overheating of Dwellings in a Temperate Climate. Energies 2021, 14, 4117. https://doi.org/10.3390/en14144117

AMA Style

Kuczyński T, Staszczuk A, Ziembicki P, Paluszak A. The Effect of the Thermal Mass of the Building Envelope on Summer Overheating of Dwellings in a Temperate Climate. Energies. 2021; 14(14):4117. https://doi.org/10.3390/en14144117

Chicago/Turabian Style

Kuczyński, Tadeusz, Anna Staszczuk, Piotr Ziembicki, and Anna Paluszak. 2021. "The Effect of the Thermal Mass of the Building Envelope on Summer Overheating of Dwellings in a Temperate Climate" Energies 14, no. 14: 4117. https://doi.org/10.3390/en14144117

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