Abstract
Climate change has increased global temperatures. When air temperature rises, it affects the condition of urban areas and creates discomfort among inhabitants of buildings. A potential sustainable approach to overcome the global warming issue is to implement green roof technology. This study aims to determine the effect of green roofs on roof thermal performance and to identify the best plant species which has the potential to lower temperatures. This study also determined the U-value, R-value, k-value and heat-flux parameters that constitute the thermal behaviour of green roofs. Three identical small-scale roof houses were constructed with one non-vegetated roof house as a control while the other two vegetated roof houses were planted with Portulaca G. and Alternanthera P., respectively. Surface roof temperatures were collected from both inside and outside the roof of each house. Results show that the average differences in temperature inside the building between the control roof and the green roof were 0.02 °C and 0.22 °C for Portulaca G. and Alternanthera P., respectively. Meanwhile, the average differences in temperature on the control roof and the green roof were 1.12 °C and 2.84 °C for Portulaca G. and Alternanthera P., respectively. The heat flux value of Alternanthera P. roof is 3.15 w/m2 better than Portulaca G. roof at 7.72 w/m2. This concludes that the roof with Alternanthera P. reduces heat that travels through the roof layer better than Portulaca G.
Access provided by Autonomous University of Puebla. Download conference paper PDF
Similar content being viewed by others
Keywords
1 Introduction
Roofs are one of the building elements most exposed to the sun as well as solar radiation [9]. Surface temperatures that rise above the ambient air temperature are a function of surface solar absorptance while surface temperatures that drop below ambient air temperature at night reflect the effect of radiative cooling such as a net heat loss by long-wave radiation to the night sky [30]. Urbanization has led to numerous global warming and climate change issues [20,21,22, 27] due to the increasing development of housing, buildings and town areas which also leads to increasing roof exposure to heat. At the same time, green areas such as forests that absorb more humidity are decreasing due to urbanization [8, 17]. Green roofs are widely known to have great potential in providing sustainable use of natural resources to reduce heat in urban areas [7, 12, 16, 29]. The presence of plants, soil and water generates different thermal properties in green roofs compared to conventional roofs [5]. Previous studies have shown the reduction of roof temperatures or heat transferred by focusing on each green roof layer and the soil media [14, 24], vegetation [3, 15, 19] and both of soil and vegetation [11]. A study by Issa et al. [14] generated the best net heat flux for a vegetated roof using two different soil media types, namely sand roof and silt clay roof at 4.7 W/m2 and 7.8 W/m2, respectively. Their study used the experimental roof to record temperature data of 8 roof layers of a green roof system using thermocouples. In order to determine the thermal properties inside the composite roof material, they used a Dual-Needle Heat-Pulse sensor which employs the following transient conduction heat transfer equation [14]:
where ρ is the material’s average density and cp is the material’s specific heat. They measured the energy of the top soil layer using Fourier’s Law.
Furthermore, Sandoval et al. [24] used the energy conservation equation to measure heat flow in a porous medium, taking into consideration the theory of fluid together with heat transport as follows:
where T is temperature; q1 is liquid flux density and qv is vapor flux density; Cw, Cp and Cv are the volumetric heat capacities of liquid water, moist soil and water vapour, respectively; λ(θ) is soil apparent thermal conductivity and L0 is volumetric latent heat of vaporisation [24]. However, these studies [3, 5, 15, 19] only monitor temperature differences using different devices for continuous temperature monitoring. Three major thermal parameters which are the R-value (the thermal resistance value), the U-value (conduction heat transfer coefficient) and the k-value (the thermal conductivity coefficient) need to be determined. The thermal properties of the green roof will then be evaluated based on temperature fluctuations and variation in heat fluxes. Therefore, following the simplest method used by previous studies, this paper examines the thermal performance of green roofs in Batu Pahat.
2 Materials and Methods
2.1 Experimental Setup and Instruments
This preliminary experiment was conducted at the Research Center for Soft Soil (RECESS), UTHM. Three identical small-scale houses were constructed using plywood material that represents the test model (Fig. 1a). Plywood is a common material used by researchers to make test models for their experiments [6, 10, 25]. The flat roof houses (at 10° slope for irrigation) were labelled as Roof A, Roof B and Roof C. The size and materials of the models should be considered as important parameters in the small-scale test. In some situations, a cubic model is used as a module for experiment. The plywood module used was 100 cm × 100 cm × 100 cm for the study thermal performance of green roofs and vertical greenery [10]. In two experiments formed and described by Binabid [6], the plywood test cell modules measured 122 cm × 122 cm × 122 cm. Test box samples by Schumann [25] had gable roof forms and they measured 175 cm × 150 cm × 100 cm. One of the experiments by Tobassom [28] used plywood models measuring 80 cm × 80 cm × 140 cm. The experiment focused more on vertical greenery systems and urban areas. Due to budget limitations, this experiment focused more on the effect of the roof’s thermal on high rise buildings. The size of small-scale roof houses built was 80 cm (L) × 80 cm (W) × 140 cm (H) (Figs. 1a and 2). Roof A which was used as the control roof represents a conventional roof, also known as a non-vegetated roof. Meanwhile, Roof B and Roof C were vegetated roofs planted with a layer of Portulaca grandiflora (Japanese rose), also known as Portulaca G. and Alternanthera paronychioides, also known as Alternanthera P., respectively. Each plant species was planted in a medium size polybag with compost soil as its medium. Retrofitting an existing bare roof with a simple green roof system might be advantageous due to its simple installation and portability [2]. Therefore, this study emphasises on the use of potted plants on rooftops in order to investigate thermal performance. All the plants were left to grow for a few weeks to ensure that they provide better shade for the roof with strong root grips. The selection of vegetation to be planted on the roofs depends on their flowering period and type of substrate these particular plants need [26].
All these three small-scale roof houses were then subjected to actual climatic conditions which include direct sunlight, wind and local rainfalls. Six units of basic USB Hygrometer data loggers (Fig. 1b) were used to collect data on temperature and humidity at intervals of 10 min due to budget restrictions. Two logger units were placed at each house to monitor both the outdoor (on the roof) and indoor (under the roof) temperatures of the roof surfaces (Fig. 2). The accuracy of surface temperatures recorded by USB Hygrometer data loggers is ±0.25 °C between 0 and 50 °C and the measuring range is between −40 and 105 °C. Although this study was conducted under a restricted budget, the use of simple instruments may still generate useful data which can be used in the future as a database.
2.2 Analysing Thermal Performance
Materials which have heat transference at low rates and high rates are known as insulators and conductors, respectively [13]. Three main thermal parameters which are normally used to measure green roofs as insulators are the R-value (the thermal resistance value), the U-value (conduction heat transfer coefficient) and the k-value (the thermal conductivity coefficient). Conduction occurs when heat is transferred between two different surfaces of a solid material with temperature difference whereas convection occurs when heat is transferred due to flowing liquid or gas [5]. Thermal conductivity is the heat transfer rate through a unit thickness of specific material per unit surface per unit temperature difference [4]. The presence of temperature difference is the basic requirement of heat transfer. Heat flux, q, is the heat transfer rate Q per unit area A and the average heat flux on a surface [5]. Heat flux comprises of the material and its temperature and the material’s depth, where ∆T is the temperature difference. A low heat flux means that there is less heat moving through the layer [5].
According to Bahrami [4], heat transfer rate is the conduction that moves through the thickness of plane wall, Δx = L of its surface area, A; over the temperature difference between these two wall surfaces, ΔT = T2 − T1; such as the following:
where k is the constant proportionality for material thermal conductivity. The higher the thermal conductivity, the greater the heat transfer. Thus, the thermal conductivity of a roof can be affected if the top of a roof is constructed with a layer of soil and plants as insulation. Previous studies about the k-values of green roof soil are limited. However, the k-value is normally based on the types and thickness of soils. The R-value (thermal resistance) is a measure of the opposition to heat transfer offered by a particular component surface of walls [18]. Green roof soil is predicted to provide better thermal insulation due to higher thermal resistance. Thermal resistance for the material is measured as follows:
where R is the thermal resistance of the material (m2 K/W), L is the thickness of the material (m) and k is the thermal conductivity of the material (W/mK). U-value (thermal transmittance) is a measure of the overall rate of heat transfer through a particular wall surface [18]. The R-value (thermal resistance) normally represents the heat flow through soil. Heat flow for green roofs usually occurs from the outer surface of a green roof to the inner surface of the roof. The U-value (W/m2 K) is measured as the following:
All the U-values, R-values and k-values are determined based on soil moisture. The moisture presence could increase the thermal conductivity of soil (k-value) since water is a better conductor than air in voids whereas the R‐value of soil should decrease [5]. However, when the soil is moist, evaporative cooling will be enhanced. In this study, the k-value refers to that of previous studies. Similar types of substrates and the thickness of extensive green roofs should be considered. By considering the moisture of the substrate of 33% due to the frequency of watering, the k-value used for this study is 0.3 w/mK [23] with green roof substrate used as the guideline.
3 Results and Discussion
3.1 Temperature Results of Roof Surface (Outdoor)
In this preliminary analysis, the experiments were only conducted for a week. Monitoring with a data interval of 10 min started from 8/5/2018 until 15/5/2018 using USB Hygrometer data loggers. Figure 3 shows the temperature results for outdoor measurements located at the rooftop of all the roof treatment types for a week. There were no drastic changes in temperature in a week. It reaches its peak temperature at 57.8 °C on 9/5/2018 where peak hours were between 12 p.m and 3 p.m.
A reduction in average temperature of 2.84 °C was recorded by the Alternanthera P. roof compared to the control roofs in a week. Meanwhile, the Portulaca G. roof had a reduction of 1.12 °C in average temperature. The average temperatures of the control roof, the Portulaca G. roof and the Alternanthera P. roof were 33.21 °C, 32.09 °C, and 30.37 °C, respectively. The highest value of 59 °C was obtained by the control roof. Meanwhile, the highest temperatures obtained by the Portulaca G. roof and the Alternanthera P. roof were 56.4 °C and 47.3 °C, respectively. In addition, the lowest values obtained in a week for the control roof, the Portulaca G. roof and the Alternanthera P. roof were 23.3 °C, 23.6 °C and 23.4 °C, respectively.
3.2 Temperature Results Under Roof Surface (Indoor)
Figure 4 shows the temperature results from indoor measurements in a week for all the 3 roof houses. The values ranged between 47 and 23.4 °C for the indoor temperatures. This indicates that the presence of plants on the roof may reduce temperatures inside buildings. However, the outdoor temperatures still rose everyday from 11 a.m. to 6 p.m. The temperatures later dropped at 6 p.m. The indoor average temperature results of the control roof, the Portulaca G. roof and the Alternanthera P. roof were 29.5 °C, 29.53 °C and 29.33 °C, respectively. The highest temperature observed on 9/5/2018 for indoor measurements was around 47 °C compared to the outdoor temperature of 59 °C which translate to a difference of 12 °C. On 9/5/2018, both the indoor and outdoor temperatures of control roofs were the highest compared to other roof types. The Portulaca G. roof had a similar outdoor temperature as the control roof, but it was 2 °C lower in terms indoor temperature compared to the control roof.
The Alternanthera P. roof had a reduction in temperature of 2.84 °C compared to the control roof in a week. Meanwhile, the Portulaca G. roof had a 1.12 °C reduction in temperature. The average temperatures of the control roof, the Portulaca G. roof and the Alternanthera P. roof were 33.21 °C, 32.09 °C and 30.37 °C, respectively. The highest value of 59 °C was obtained during the week by the control roof. Meanwhile, the highest values obtained by the Portulaca G. roof and the Alternanthera P. roof were 56.4 °C and 47.3 °C, respectively. In addition, the lowest values obtained during the week for the control roof, the Portulaca G. roof and the Alternanthera P. roof were 23.3 °C, 23.6 °C and 23.4 °C, respectively.
3.3 Temperature Differences Between the Inner and Outer Roof Surfaces for Portulaca G. and Alternanthera P.
Figure 5 shows the results obtained for temperature difference between the indoor roof surface and the outdoor roof surface for Portulaca G. The average temperature difference between indoor and outdoor roof surfaces for Portulaca G. was 2.55 °C.
Figure 6 shows the results obtained for the temperature difference between the indoor roof surface and the outdoor roof surface for Alternanthera P. The average temperature difference between the indoor surface and the outdoor surface for Alternanthera P. was 1.04 °C. This result shows that the heat conductivity of the Alternanthera P. roof is slightly less than that of the Portulaca G. roof.
Table 1 indicates the thermal conductivity of plywood at 0.138 W/mK [1] with a soil cover for Portulaca G. roof and Alternanthera P. roof at 0.30 W/mK [23] when the moisture content of soil of 33% is taken into consideration. The heat flux values for Portulaca G. and Alternanthera P. were 7.72 W/m2 and 3.15 W/m2, respectively. It shows that Alternanthera P. has a better heat flux than Portulaca. G. This may be due to the physical characteristics of each vegetation.
4 Conclusions
From the results, the temperature reduction of small-scale green roof houses for all roof treatment does not show any major difference as the temperature difference recorded ranged between 1.0 and 3.0 °C for both indoor and outdoor temperatures. Furthermore, the temperature difference between indoor and outdoor roof surfaces also recorded a similar range between 1.0 and 3.0 °C for both vegetated roofs. This may be due to the size of the small scale houses where the wall temperature may affect the indoor temperature performance. Wall insulation should be taken into consideration for future experiments. Meteorological parameters can potentially influence the results and should be monitored in future studies. It is also suggested that vegetation with better shade, bigger leaves or shrubs may provide more temperature reduction. The thickness of the soil medium without polybags should be also considered as polybags might absorb more heat than normal rectangular boxes.
References
ASHRAE (1967) Handbook of fundamentals. American Society of Heating, Refrigerating and Air-conditioning Engineers Inc., Atlanta
Asmat I (2010) Potted plants on flat roof as a strategy to reduce indoor temperature in Malaysian climate. Am J Eng Appl Sci 3(3):534–539 (2010)
Barozzi B, Bellazzi A, Pollastro MC (2016) The energy impact in buildings of vegetative solutions for extensive green roofs in temperate climates. Building: Article, MDPI
Bahrami M (2019) Steady conduction heat transfer. Online notes. Simon Fraser University, Canada
Becker D, Wang D (2011) Green roof heat transfer and thermal performance analysis. In: Civil and environmental engineering. Carnegie Mellon University
Binabid, J. (2010). Vertical garden: the study of vertical gardens and their benefits for low-rise buildings in moderate and hot climates. M.B.S. University of Southern California
Coma J, Pérez G, Cabeza LF (2018) Green roofs to enhance the thermal performance of buildings and outdoor comfort (Chap. 3.2). In: Nature based strategies for urban and building sustainability, pp 109–117
Cui N, Feng CC, Wang D, Li J, Guo L (2018) The effects of rapid urbanization on forest landscape connectivity in Zhuhai City, China. Sustainability: Article, MDPI
Divsalar R (2010) Building problems in hot climates. Master thesis of science in architecture, University of Eastern Mediterranean, North Cyprus
Figueroa M (2008) Green roof performance in Los Angeles, California. M.B.S. University of Southern California
Gaffin SR, Khanbilvardi R, Rosenzweig C (2009) Development of a green roof environmental monitoring and meteorological network in New York City. Sens Commun 9:2647–2660
Gargari C, Bibbiani C, Fantozzi F, Campiotti CA (2016) Environmental impact of green roofing: the contribute of a green roof to the sustainable use of natural resources in a life cycle approach. Agricult Agricult Sci Procedia 8:646–656
Hassall DNH, Richards FR (1977) Reflective insulation and the control of thermal environments. St. Regis—ACI
Issa RJ, Leitch K, Chang B (2015) Experimental heat transfer study on green roofs in a semi-arid climate during summer. J Constr Eng 2015
Jim CY (2012) Effect of vegetation biomass structure on thermal performance of tropical green roof. Landsc Ecol Eng 8:173–187
Kasmin H, Yusoff NA, Samsudin MH, Atan N, Kassim R, Ahmad H, Sayuti Z, Abdullah F (2015) Preliminary overview on thermal performance of green roof. Appl Mech Mater 773:1047–1052
Liang YQ, Li JW, Li J, Valimaki SK (2008) Impact of urbanization on plant diversity: a case study in built-up areas of Beijing. For Stud China 10(3):179–188
McMullan R (1992) Environmental science in building, 3rd edn. The Macmillan Press Ltd., London
Morau D, Libelle T, Garde F (2012) Performance evaluation of green roof for thermal protection of buildings in reunion Island. Energy Procedia 14:1008–1016
Mohd Zahudi Z, Adnan MS, Amat NF, Erfen Y, Che Ali N (2015) Climate change impacts on rainfall distribution at Teluk Intan catchment. Appl Mech Mater 773–774:1296–1300
NASA (2019) The effects of climate change. In: Global climate change: vital signs of the planet
Rahmat SN, Jayasuriya N, Adnan MS, Bhuiyan M (2016) Analysis of spatio-temporal trends using standardised precipitation index (SPI). ARPN J Eng Appl Sci 11(4)
Sailor DJ (2008) @@Thermal property measurements for ecoroof soils common in the Western U.S. Energy Build 40:1246–1251
Sandoval V, Suárez F, Vera S, Pinto C, Victorero F, Bonilla C, Gironás J, Bustamante W, Rojas V, Pastén P (2015) Impact of the properties of a green roof substrate on its hydraulic and thermal behavior. In: 6th international building physics conference, IBPC 2015. Energy Procedia 78:1177–1182
Schumann L (2007) Ecologically inspired design of green roof retrofit. M.S University of Maryland, College Park
Spala A, Bagiorgas HS, Assimakopoulos MN, Kalavrouziotis J, Matthopoulos D, Mihalakakou G (2008) On the green roof system. Selection, state of the art and energy potential investigation of a system installed in an office building in Athens, Greece. Renew Energy 33(1):173–177
Sun Q, Miao C, Hanel M, Alistair GLB, Duan Q, Ji D, Li H (2019) Global heat stress on health, wildfires, and agricultural crops under different levels of climate warming. Environ Int 128:125–136
Tobassom S (2014) Thermal impacts of vertical greenery systems. Environ Clim Technol. https://doi.org/10.1515/rtuect-2014-0007
Yang J, Mohan Kumar D, Pyrgou A, Chong A, Santamouris M, Kolokotsa D, Lee SE (2018) Green and cool roofs’ urban heat island mitigation potential in tropical climate. Sol Energy 173:597–609
Yannas S, Erell E, Molina JL (2006) Roof cooling techniques a design handbook. Earthscan, London
Acknowledgements
The authors would like to acknowledge the financial support provided by Universiti Tun Hussein Onn under the Postgraduate Incentive Research Grant (GIPS—1351) and the Exploratory Research Grant Scheme (ERGS—E052) which made this study possible. The authors would also like to thank the Research Centre for Soft Soil (RECESS), UTHM, for the opportunity to use its laboratory sites for the green roof test beds.
Author information
Authors and Affiliations
Corresponding author
Editor information
Editors and Affiliations
Rights and permissions
Copyright information
© 2020 Springer Nature Switzerland AG
About this paper
Cite this paper
Yacob, M.N.M., Kasmin, H., Kori, M.K.A.M., Mohamed, W.A.W., Rahmat, S.N., Adnan, M.S. (2020). The Influence of Extensive Green Roofs on Roof Thermal Performance in Batu Pahat Climate. In: Mohamed Nazri, F. (eds) Proceedings of AICCE'19. AICCE 2019. Lecture Notes in Civil Engineering, vol 53. Springer, Cham. https://doi.org/10.1007/978-3-030-32816-0_112
Download citation
DOI: https://doi.org/10.1007/978-3-030-32816-0_112
Published:
Publisher Name: Springer, Cham
Print ISBN: 978-3-030-32815-3
Online ISBN: 978-3-030-32816-0
eBook Packages: EngineeringEngineering (R0)