1. Introduction
There is growing concern for global energy consumption due to the adverse environmental impacts, insufficient energy resources, difficulties in supply, and economic growth [
1]. Among all the energy consumption sectors, the building sector is one of the largest sectors and contributed to 32% of energy consumption used globally in 2010 and contributed to one third of greenhouse gases [
2,
3]. Green roofs are becoming a prevalent development option for buildings and are considered to have good potential for decreasing the building indoor cooling and heating loads. Green roofs also have numerous environmental, social, and economic benefits as well. Research has shown that green roofs can reduce stormwater runoff and the urban heat island effect, provide habitat for wildlife, enhance air and water quality, reduce the energy consumption of buildings, and reduce noise pollution [
4,
5,
6]. A green roof is a roof that is covered with a growing medium (the substrate layer), vegetation, as well as other functional layers (e.g., drainage layer and filter layer) [
7]. Among all the layers of a green roof, the vegetation layer and the substrate layer are the most important layers; thus, they need to be strategically selected to maximize the many benefits of a green roof.
The substrate layer plays an important role in water runoff reduction, peak flow reduction, water quality improvement, and thermal benefits. Based on the thickness of the substrate, a green roof can be divided into three categories: intensive (above 12 inch or 30 cm), semi-intensive (6–12 inch or 15–30 cm), and extensive (3–6 inch or 8–15 cm) [
4,
8]. The intensive green roof has a higher water holding capacity and more plant options including small trees and shrubs; however, this requires more maintenance, irrigation, fertilization, as well as more consideration to building structural support. Compared with the intensive green roof, the extensive green roof is more common globally because of its low maintenance, nutrient and irrigation requirements.
The vegetation layer plays an important role in improving runoff water quality [
9], reducing heating effects [
10], and providing animal habitat. In the selection of vegetation, geographic location, wind, humidity, temperature, rainfall, and sun exposure should all be considered while noting that the choice of plant species is also influenced by the designed soil thickness. Many studies have focused on the selection of suitable plants [
11,
12], with most agreeing that sedum species are good options for extensive green roofs all over the world, since they can survive under a variety of conditions. Teeri et al. [
13] indicated that Sedum
rubrotinctum R. T. Clausen can survive for 2 years without water, while Durhman et al. [
14] indicated that Sedum can survive and maintained active photosynthetic metabolism after 4 months without water. Succulents can also survive through droughts because they store water in their stems and leaves [
15].
Many studies have investigated the energy performance of vegetated green roofs. Vera et al. [
16] studied the influence of an extensive green roof on the retail stores’ thermal performance using EnergyPlus 8.6.0 (NREL, Department of Energy, Washington DC, MD, USA). Mahmoodzadeh et al. [
3] studied the effects of green roofs on school buildings energy performance using EnergyPlus 8.8. Both studies note limitations in the EnergyPlus program, such as the fact that substrate moisture content varies over time, but substrate thermal properties are held constant over time. These result in a lack of accuracy in substrate thermal properties that are input to the model. In general, these approaches are plagued by a variety of problems including inaccuracy in model inputs of substrate thermal properties and lack of knowledge of the role of the substrate separate from the vegetation. Regarding the lack of accuracy in substrate thermal properties that are input to the models, it is well known that substrate thermal properties such as thermal conductivity, specific heat capacity, albedo play important roles in soil energy balance. Those parameters are influenced by substrate density, porosity, temperature, and in particular, moisture content. The substrate’s density and porosity are substrate specific and may be indirectly related to temperature and moisture content. While, the temperature and moisture content are a function of the weather and environmental conditions, irrespective of the substrate.
Low porosity makes heat transfer through the substrate easier because the particles are compressed tighter, resulting in a greater number of interior contact points that aid higher conduction heat transfer [
17,
18]. Soil thermal performance varies as moisture content changes because water will replace the air among soil particles and connects the gaps between them [
19]. Temperature also plays an important role in thermal performance, especially in the phase transition zone [
20]. According to the energy balance study of green roof, substrate parameters that are critical to green roof energy budget are density, thermal conductivity, specific heat capacity, emissivity, and albedo. Pianella et al. [
6] noted that many studies that were analyzing variations in thermal conductivity, did so using transient measurements. Transient measurements are made when the measurand, or factors affecting the measurand, vary with time [
6]; which can give rise to uncertainty and error. In steady-state observations on the other hand, the measurand has reached an equilibrium or steady-state condition in which the measurand or influencing factors, do not change over time. This gives rise to consistent observations necessary for modeling and inference. Pianella et al. [
6] compared transient vs. steady-state measurement and found that steady-state measurements are more consistent within replicates and provides more accurate results as compared with transient measurements.
As noted, there is a lack of information and research on the energy performance of the substrate alone. Although many researchers have studied the thermal and energy performance of green roofs, very few have focused on the performance of the substrate in isolation. This would be important in many climates in which the vegetation is inactive or less active in energy and water budgets for a portion of the year. In the fall and winter months, which is the case in many parts of Canada, the substrate is the only “active” layer year-round, and may undergo freezing and thus, its thermal conductivity may change with temperature and moisture content prior to freezing. There is a lack of studies on the thermal performance of the substrate in isolation, particularly during freeze–thaw periods. Therefore, further understanding the substrates’ role in the energy and water budget of a green roof in these periods requires isolating the substrate layer from the vegetation layer in any numerical or experimental study. This will provide insight to improving estimates of the parameters used to model energy and moisture budgets in green roof systems.
Many parts of Canada are exploring or adopting green roof technology through either retrofitting old buildings with green roofs or installing green roofs on new buildings [
21]. In Toronto, Ontario, Canada, for example, the relevant by-law required new buildings larger than 2000 m
2 to green 20–60% of the building rooftop [
21]. As green roofs are increasing in popularity due to the numerous environmental, social, and economic benefits, design methodologies that can realistically achieve the benefits afforded by this technology are being sought for application in all Canadian climates. Therefore, to better support the design process given the literature review above, the objective of this research is to is to study the thermal performance of the substrate in a green roof as it is affected by temperature and moisture content. An experiment into the thermal conductivity at different temperatures and moisture contents was performed using four different commercially available substrates for green roofs. Additionally, experiments on two equally sized, experimental green roof test cells constructed in Victoria, BC were used to investigate the thermal performance of substrate and green roof related design parameters in an outdoor environment. The substrates examined are specifically available and proposed for use in Canadian climates. The lab experiments will provide users information on aspects unique to these substrates and results will be compared to other studies using similar substrates that are looking at the role of moisture content on thermal conductivity. This will also support parameterization of these substrates in energy models. The outdoor experiments will further explore the use of these substrates in green roofs for modifying interior temperatures. These experiments will also support an unconventional modeling approach in which the green roofs studied are modeled as first-order dynamic systems that respond to exterior temperatures depending on the roof’s condition (determined by factors including moisture content, substrate, roof design, vegetation and irrigation). By determining and comparing the time constants of each first-order system, more definitive conclusions can be drawn on the role of these influencing factors on the green roof’s role in energy budgeting.
4. Conclusions
Results of the experimental study into the thermal conductivity at different temperature and moisture contents show that at the same temperature and moisture content, Eagle Lake has the highest thermal conductivity while Sopraflor I has the lowest thermal conductivity. It appears, based on the results available from this study, irrespective of temperature or moisture content, the substrate with higher dry density has higher thermal conductivity. This is consistent with the test performed by Barozzi et al. [
34]. More research should be performed, however, to further study the relationship between dry density and thermal conductivity for other substrates, as porosity also influences substrate dry density and thermal conductivity. With temperature change and in an unfrozen state, the Mann–Kendall trend test (M-K test) showed there is no significant relationship between thermal conductivity and temperature. An ANOVA test was also applied given the low number of data points used in the M-K test and the ANOVA results confirmed this outcome. Results from Zhang et al. [
20] also showed that for the thawed substrates, the influence of temperature on the thermal conductivity can be neglected, while in the phase transition zone, thermal conductivity increases significantly as temperature decreases to below zero. This was also observed when combining all data in both frozen and in unfrozen states. In the phase transition zone (between +5 and −10 °C), as temperature decreases, thermal conductivity increases sharply during the transition from water to ice because of the difference in thermal conductivity difference between the two phases. In general, when in the unfrozen state and as moisture content changed, thermal conductivity increased linearly as moisture content increased. Clarke et al. [
29] also showed a simple linear regression fit for the thermal conductivity of three different substrates as a function of moisture content. In the frozen state, however, an exponential function exists between thermal conductivity and substrate moisture content prior to freezing.
Results of the experimental study on the substrate thermal performance show that bare roofs and extensive roofs act very differently in terms of response to changes in outdoor temperature. Roof albedo affects the amount of solar radiation available for absorption/transmittance, and the bare roof, which had the lowest albedo of all tested roofs, would be subject to greater heating than the green roofs, which have slightly higher albedos (although only marginally higher). Beyond the amount of solar radiation absorbed, a roof’s response to outdoor temperature is then dictated by the thermal conductivity of the roof layer as a whole. As outdoor temperature fluctuated sinusoidal each day, it was found that compared with the bare roof, the extensive roof has 75% reduction on the amplitude of the interior temperature. Compared to the extensive roof, there is a further 40% reduction in the amplitude of the interior by the intensive roof. In addition, interior temperature decreased when irrigated as compared to conditions without irrigation. When a sedum mat was added above the substrate, there was a 20% reduction in the amplitude of the interior temperature compared with the cell without the sedum mat.
All of these results point to the need to consider both moisture effects and seasonal variability in the design and maintenance of green roofs. The laboratory experiment examining the relationship between moisture content and thermal conductivity and provided mathematical functions for thermal conductivity as a function of moisture content for frozen and non-frozen conditions (seen in
Table 3). Energy transfer models of actual green roofs that currently use static values of thermal conductivity can now simply modify the thermal conductivity as a simple mathematical function of moisture content. Additionally, mathematical functions were found that neatly related thermal conductivity as a function of temperature when temperature moved from a frozen to a non-frozen state. These can provide information on how to parameterize thermal conductivity for a green roof in the winter time when conducting energy and temperature simulations for a building with a green roof.
The outdoor, small test cells were useful because they allowed for a clear understanding of the effects of the studied substrates, and the potential for vegetation, on modulating interior temperature in comparison to bare roofs. By reducing the roof to a first-order dynamic system—effectively a one parameter (τ), black-box—comparisons could be made between roofs more simply. Each roof’s behavior was reduced to values of τ and changes in temperature amplitude and phase. By simply expressing the interior temperatures as the same sinusoidal functions but with different amplitudes and phases, one can use these simple black box models to illustrate the importance of certain design parameters over others in designing a green roof. In this study, this black-box modeling showed that any green roof is a marked improvement in insulative value over no green roof, but the extra 50 mm of substrate thickness was marginally helpful, and thus, the thinner, extensive green roof is sufficient. Similarly, the results showed that incorporating changes in moisture content either through irrigation or rainfall is an important consideration in modelling or predicting interior air temperatures.
Understanding these important effects on thermal balance can facilitate resilient responses to climate change by affecting how we design green roofs. Future research extending this work should consider scale effects due to the size of the test cells used outdoors; observations taken over a greater range of temperature changes including sub-zero temperatures; modeling outdoor green roofs to include a dynamic thermal conductivity as a function of moisture content in energy budget models.