An investigation of sensible heat uxes at a green roof in a laboratory setup Tahir Ayata a, b, * , Paulo Cesar Tabares-Velasco a , Jelena Srebric a a Department of Architectural Engineering, Pennsylvania State University, University Park, PA 16802, USA b Kayseri Vocational College, Erciyes University, 38039, Turkey article info Article history: Received 21 September 2010 Received in revised form 13 January 2011 Accepted 13 March 2011 Keywords: Green roof Sensible heat ux Passive cooling Volumetric water content Evapotranspiration Convection correlations abstract During the last few years, several models have been proposed for the calculation of green roof thermal behavior, but the validation studies of such models are lacking a comprehensive set of highly accurate data. In this study, an experimental laboratory setup was used to create different environmental conditions and to measure sensible heat uxes to/from a vegetated roof assembly. This experimental setup has been successfully used for different wind velocities (0e3 m/s) to create free and forced convection conditions around green roof tested samples. Furthermore, our study proposed a basic modelfor calculations of the convective heat transfer at green roof assemblies, which is a modied version of the Newtons cooling law, calibrated and then validated with different sets of data. For forced convection ow regimes, the proposed basic modelresulted in RMSE (Root Mean Square Error) of 11 W/m 2 and R 2 value of 0.81. Similarly, the model provided RMSE of 6.6 W/m 2 and R 2 of 0.90 for sensible heat uxes with free convection conditions. In the future, this model will be used in on-site experimental studies to understand its performance under wind conditions that exhibit a much wider range than the studied velocity range near the leaf canopy. Ó 2011 Elsevier Ltd. All rights reserved. 1. Introduction Vegetation has been used on building roofs and walls since ancient times, with the most famous example of the Babylonian gardens in Mesopotamia. A widespread use of roof vegetation has signicantly increased in recent years. Fig. 1 shows an example of contemporary use of vegetation for a traditionally-designed house in Norway. Some European countries have explored opportunities for use of extensive green roofs since the 1970s [1]. The specic purposes of green roof installations vary, but generally hinge upon stormwater reduction or improved building energy efciency and often both. As stormwater concerns in urban settings have become ubiquitous, green roofs have been introduced as a viable and effective method for reducing urban stormwater runoff from roof surfaces [2]. The types of growing media and roof assemblies vary, but most green roofs consist of a drainage layer, a root barrier, and awater- proof membrane as shown in Fig. 2. A green roof growing media depth is typically between 0.05 and 0.3 m [3], while the vegetation layer can incorporate different plants depending on the local climate [4]. A green roof has numerous benets that include improved air quality, reduction of the heat-island effect,sound attenuation, building envelope protection, esthetic value, and stormwater detention, in addition to the reduction of energy absorbed by the roof assembly [2,5e7]. One of the ecological functions a green roof provides is its stormwater management capacity. Nevertheless, to take full advantage of green roofs, building designers need quantitative assessments of green roof benets. Horizontal building surfaces, such as roofs, experience high thermal loads during summer conditions in climates such as the Mediterranean or some U.S. climate regions. Green roofs may offer an adequate solution to this problem [8]. Theoretical and experi- mental analyses of different roof assemblies to promote cooling mostly focuses on evaporative and radiative heat transfer mecha- nisms. The green roof vegetation shades this type of roof assemblies from direct solar radiation, and it also cools the roof by means of evapotranspiration from the vegetation layer [9]. The vegetation layer also absorbs large quantities of solar energy during the diurnal biological functions. An incoming amount of solar radiation can affect the internal temperature of a building. Out of the total incoming solar radiation, approximately 27% is reected, 60% is absorbed by the plants and the soil through evaporation, and 13% is transmitted into the soil [10,11]. As a result, green roofs can control the temperature of the roof assembly and protect the roof membrane from temperature extremes. During summer weather * Corresponding author. Department of Architectural Engineering, Pennsylvania State University, University Park, PA 16802, USA. E-mail address: tahirayata@yahoo.com (T. Ayata). Contents lists available at ScienceDirect Building and Environment journal homepage: www.elsevier.com/locate/buildenv 0360-1323/$ e see front matter Ó 2011 Elsevier Ltd. All rights reserved. doi:10.1016/j.buildenv.2011.03.006 Building and Environment 46 (2011) 1851e1861