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Article

Impact of Green Roof and Orientation on the Energy Performance of Buildings: A Case Study from Saudi Arabia

Architectural Engineering Department, King Fahd University of Petroleum and Minerals, Dhahran 31261, Saudi Arabia
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Author to whom correspondence should be addressed.
Sustainability 2017, 9(4), 640; https://doi.org/10.3390/su9040640
Submission received: 30 January 2017 / Revised: 28 March 2017 / Accepted: 13 April 2017 / Published: 18 April 2017
(This article belongs to the Section Energy Sustainability)

Abstract

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Saudi Arabia is one of the largest countries in the Middle East region in terms of population, geographic area and scale of economy. It has a fast growing energy sector with over 76% of the total electricity being consumed in the building sector. Domestic buildings account for 51% of total electricity consumption. Predominantly due to hot climatic conditions, most of the energy consumption in buildings is attributed to the heating, ventilation and air conditioning (HVAC) loads. In terms of supply mix, the country entirely relies on oil and gas to meet its energy requirements. The high growth in energy demand is imposing stringent energy, environmental and economic challenges for Saudi Arabia. The present work aims to explore prospects of energy saving in buildings through the application of green roof technology. With the help of ECOTECT modelling, the work examines the effectiveness of green roof on considering modern faculty homes built in the King Fahd University of Petroleum and Minerals situated in the hot-humid climatic conditions of the Easter Province of the country. The same building has also been investigated for the hot-dry climate of Riyadh, the capital city. The work also examines the impact of orientations on the energy performance of buildings.

1. Introduction

The global concerns on energy and environmental challenges are becoming ever more important. Growing demand for energy, depletion of natural resources and global warming are leading problems in this respect [1,2]. Global warming and climate change are leading to wide-ranging challenges including sea level rise, seasonal disorder and natural catastrophes [3,4]. The building sector has an important role in the international energy and environmental scenarios as it consumes almost 40% of energy and results in over a third of greenhouse gas (GHG) emissions [5]. The building sector is experiencing a rapid growth in countries across the world due to factors like population growth, infrastructure development, modernization and urbanization. To tackle the facing of energy and environmental problems, the world is aiming to promote sustainable development as is reflected by the recent global agreement on climate change, COP21 [6]. The building sector has a crucial contribution to make towards improving sustainability standards and addressing the energy and environmental challenges. In the backdrop of the global drive for sustainability, buildings are facing significant improvement in their energy efficiency standards especially in the developed countries. Efforts are being made both on the policy and technological fronts. While buildings performance regulations and standards are being made stringent through robust policy frameworks, technological advancements are improvising effective solutions to help the cause.
Saudi Arabia is one of the largest countries in the Middle East in terms of geographic area, economy and infrastructural development. Owing to factors like increasing population, modernization and economic development, the energy demand in the country is rapidly surging. Estimates suggest that between 2000 and 2014, the primary energy demand increased by over 100%. Buildings account for almost 80% of the total electricity consumption in the country. The residential buildings alone consume almost 50% of the total national power generation [1]. Owing to its rich oil and gas reserves, it has traditionally cherished heavily-subsidized energy tariffs. The situation however is fast changing. As of the recently announced strategic policy framework, Vision 2030, there are targets to remove 200 billion Saudi Riyals of energy subsidies by 2020 [7,8]. The situation is bound to bring a paradigm shift in the energy consumption patterns. The role of energy conservation strategies and energy efficiency measures is set to become critical. Green roofs can be applied as an energy saving options in Saudi Arabia.
Green roofs are a passive strategy that can be a useful solution in different climates to reduce energy consumption in buildings. It offers energy saving and reduction in GHG emissions while enhancing the aesthetic qualities and architectural presentation of buildings [9]. It is being used as an energy saving measure in countries around the world [10,11]. Although it can reduce the energy demand in different climatic conditions, its performance mainly depends on climatic conditions, building function, insulation of the building envelope and the type of green roof [12]. Green roofs not only protect the roof from solar radiations and extensive heat fluctuations, but also maintain the indoor temperature by working as insulation. In summer, it reduces the indoor air temperature of the building by providing shading, insulation and evapotranspiration against the solar radiation, while in winter, it works as a wind shield to reduce the heating loads, but the winter effect is less than the summer effect.
The present work aims to investigate the prospects of the green roof, a passive energy saving option, in hot climates by focusing on the climatic conditions of Saudi Arabia. Its main objectives are as follows:
  • To examine the effectiveness of the green roof in hot climates in terms of energy saving.
  • To determine the impact of building materials in improving energy performance of buildings.
  • To study the influence of the orientation on the energy performance of buildings.
The above parameters have been investigated for modern residential villas situated in the city of Dhahran. It is also important to mention that we are considering the same building in the Riyadh climate, as well. Basically, Saudi Arabia has three main population bases, Dhahran/Dammam, Riyadh and Jeddah. The twin cities of Dhahran and Dammam are situated on the east coast of the country, while Jeddah is on the west coast. Both of these locations have quite similar climates, hot and humid. The study has therefore chosen one of these locations, Dhahran, as the representative of the hot and humid climate. Riyadh, on the other hand, has a predominant hot and dry climate. ECOTECT software has been used to model the energy performance of these villas with wide ranging features.

2. Project Brief

The King Fahd University of Petroleum and Minerals situated in the city of Dhahran in Saudi Arabia is one of the largest universities in the Middle East region. Owing to its on-campus huge infrastructure consisting of academic and administration blocks, faculty and student residential buildings, community centers, schools, workshops and warehouses, it presents an urban scale environment. Already having over 1000 residential units for faculty and staff, it has constructed 200 new villas for faculty. Most of these new villas are positioned north-south while some are oriented northeast-southwest. A small proportion of villas also face northwest, as shown in Figure 1.
Each villa consists of two stories with almost 450 m2 of built-up area. The clearance height of each story is 3 m. Main facilities provided on the ground floor are guest room, kitchen, dining, family dining, laundry, toilets, store and service area, as shown in Figure 2a, while on first floor, four bedrooms are provided with two attached baths and one shared toilet, as shown in Figure 2b. The window-wall ratio (WWR) is almost 10%. The structural members on the external facade are concrete masonry units (CMU), hollow blocks, while the roof is constructed with reinforced cement concrete (RCC) slab and some other composite materials. Windows are double glazed with aluminum frame. The HVAC system used in these residential buildings is a constant-volume DX unit, while two separate units are installed on the rooftop, one for each floor. The capacity of the HAVC system at the ground floor is 11.9 tons, and the supply of air flow is approximately 11.3 ACH. The capacity of the HVAC system on the first floor is 9.4 tons, and the supply airflow is 9.4 ACH. The lighting power density at the ground floor and first floor is respectively 21 W/m2 and 13 W/m2.

3. Literature Review on the Green Roof

Green roofs are one of the passive strategies used to reduce the heat transfer and improve the thermal comfort of a building or space by application of vegetation on the roof. It not only reduces the direct and diffuse radiation incidences on the roof [13], but also improves the life span of the roof by modifying the temperature fluctuations experienced by its different layers, as it reduces the thermal stresses and heat aging of roof components [14]. Green roofs are basically composite structures in which plants are provided above a soil layer. Below the soil layer, a filter is provided to stop the soil from washing. Rain water storage, which is plastic profile elements, substituting draining gravel, is provided to store water for plants for the dry season. It also takes surplus water to the roof gutter. A root barrier is provided underneath the drainage layer to protect the water-proofing membrane [15]. Alternatively, offsite prefabricated growing medium in the form of blocks can also be used with plants already sprouted. In this case, the block can be easily removed for maintenance purposes [16]. There are three types of green roofs, extensive, semi-intensive and intensive green roofs. The intensive green roof is relatively heavy weight construction, provided on thick growing media (soil), and it requires more maintenance because of the types of plants used, as it creates a garden-like environment [17]. On the other hand, the extensive roof is light weight construction, which requires less maintenance and little human intervention because of less variety of plant types.
Studies show that the green roof is more effective in a hotter and drier climate as urban heat temperature can be reduced more effectively [18]. Green roofs are more effective at reducing the heat gain than heat loss, as according to a study, 70–90% of the heat gain was reduced in summer, while 10–30% of heat loss in winter [19]. From one of the studies made on a residential building in Cairo, it was found that the cost saving of the green roof as compared to the conventional roof is between 15 and 32% [20]. From another study, made in Jordan, it is concluded that 17% of the HVAC energy demand can be reduced by using the green roof [21]. In another research done in a Mediterranean climate, a 6–49% reduction in energy demand was noticed because of the green roof [22]. Green roofs can also reduce storm water management by 40%, as according to a research undertaken in Singapore, the green roof can reduce the peak flow by 65% and retain overall runoff by 11.6% for a maximum 1-mm/min rainfall intensity [23]. A surface temperature difference between the green roof and the conventional roof was noted as an average of 20 °C [14]. In a research conducted on porous tiles in Guangzhou China, it is noted that the thermal performance of the roof is influenced by moisture content in the porous tiles. The surface temperature of the roof can be decreased up to 11.3 °C if porous tiles contain a sufficient amount of water [24]. In the case of the green roof, there is not only a soil layer containing moisture content, but also plants provide shading above the whole roof surface.
There are many factors affecting green roof design, like thermal conductivity, specifics heat, density, thermal absorptance, solar absorptance, height of plants, leaf area index, etc. A 150 mm–1200 mm soil depth is required for the intensive green roof to support large plants, while growing media required for the extensive roof can be 50–150-mm thick [19]. Moreover, the typical weight of the intensive green roof is almost 290 kg/m2–968 kg/m2, while for the extensive green roof, it is from 20 to 169 kg/m2 [25]. The purpose of the thick soil layer is to create thermal mass, which not only increases the time lag, but also reduces thermal transmittance. Furthermore, soil depth, organic matter and water balance in the soil layer affect the soil thermal performance [26]. According to a study, a 10 cm-thick soil layer is enough to control the heat penetration [19]. Another research work done in Singapore reveals that the thermal resistance of roof can be increased by 0.4 KW for every 10-cm increase in the thickness of the substrate layer with clay [27]. Water content the in soil layer also changes the thermal properties of it, as more water content can increase the thermal conductivity of the layer [28]. Organic matter in soil also maintains good soil structure [29]. Required benefits from plants can be achieved by providing proper irrigation [30].
The vegetation layer not only creates good aesthetics, but is also good for the environment [31]. A change in the physical characteristics of plants changes the impact on the environment. In a harsh climate, only limited species of plants can survive. Plants’ survivability in a hot climate also depends on the availability of irrigation [32]. In a research work, after studying twelve different species (forbs, sedum and grasses) commonly used for extensive green roofs, in three different combinations of plants and three different water regimes (wet, moderate and dry), it is concluded that under dry conditions, a diverse plant mix has greater survivability than a monoculture [33]. Moreover, sedums have better drought tolerance than forbs and grasses. According to another study, the survival of plants depends on plant water use, leaf succulence and substrate properties. Plants with high water holding capacity and high succulence leaves survive longer [32]. Moreover, the mean thermal conductivity value for leaves varies from 0.268 to 0.58 W/m2K [17].

4. Climatic Analysis of Saudi Arabia and the Application of the Green Roof

Mostly, Saudi Arabia has a desert climate with extreme heat during the day and an abrupt temperature drop during the night and low average annual rainfall, except in the province of Asir, along the western coast, where an average of 300 millimeters of rainfall occurs from October to March. The average summer temperature in Saudi Arabia is 45 °C and can go up to 54 °C [34]. The average temperature during spring and autumn is 29 °C, while in winter, it rarely drops to 0 °C. Now, from the literature review, it is clear that green roofs reduce the cooling load more significantly than heating loads [19]. This is because of the plant foliage, which absorbs most of the solar radiation and makes foliage hotter than the surrounding temperature. Additionally, the heat transfer to the roof system is reduced as the substrate layer gets further cooled because of evapotranspiration. Hence, the green roof can be very effective in the Saudi climate, which mostly has hot weather. Moreover, it can not only be applied in new buildings, but also old buildings on the existing roof structure with only the addition of green roof layers, and hence, it can be really helpful in reducing the Saudi buildings’ energy demand.

4.1. Dhahran Climate

Dhahran has a hot desert climate. The area within 40 km of this station is covered by oceans and seas (77%), lakes and rivers (14%), shrublands (6%) and built-up areas (3%) [35]. Normally, summer duration is from 15 May to 28 September, and the average daily high temperature is above 38 °C. The hottest day of the year, typically falling in July, has an average high temperature of over 43 °C and average low temperature of around 30 °C. On the other hand, in winter, the average daily high temperature is below 25 °C, while the winter duration is from 3 December to 4 March. The coldest day, typically towards the end of January, has an average high temperature of 20 °C and a low of 11 °C. The daylight hours on the shortest and longest days of the year, 21 December and 20 June, are respectively 10.5 h and 14 h. From the end of November, the sky starts becoming cloudier, while from the start of May, it starts appearing clearer. Over the year, relative humidity varies from 15% to 90%. Wind speed typically varies between 0 and 9 m/s. Precipitation occurs in the form of light rain, moderate rain and thunderstorms. Mostly, it is observed as moderate rain, which is almost 46% of the total precipitation days [35]. During summer, from 15 May to 28 September, there is almost a 2% average chance that at some point during a given day, precipitation will occur, while there is an 18% average chance that precipitation will occur at some point during a given day in winter, which starts from 3 December and ends on 4 March.

4.2. Riyadh Climate

In contrast with Dhahran, Riyadh’s climate is hot and dry. Temperature variation throughout the year is between 8 °C and 43 °C. The average daily high temperature is above 39 °C during summer, which starts on 14 May and ends on 26 September. The average high temperature is 43 °C, while the low is 28 °C on the hottest day of the year ,which is in August [36]. The average daily high temperature is below 24 °C during winter, which lasts from December–February. On the coldest day of the year, which is typically in January, the average high and low temperatures are 19 °C and 8 °C, respectively. Like Dhahran, daylight is also available in Riyadh for almost 10.5 h on the shortest day of the year, which is 21 December, while on 20 June, which is the longest day of the year, it is available for almost 14 h. Relative humidity in Riyadh normally changes from 6% to 71% during the year, but sometimes, it may reach 96% as the high and can drop to 3% as the low. Typical wind speed is between 0 m/s and 7 m/s. Mostly, the wind is blowing from north almost 17% of the time, and 11% of time, it is also coming from the northwest. Ten percent of time, wind is also coming from the south, while 12% of the time, it is also blowing from the southeast. There are 12% and 2% average chances that moderate rain occurs during winter and summer, respectively.

5. Material Used

In this section, we will discuss the material used in this faculty housing project and our proposal for the green roof section. In the external wall section, 100 mm-thick CMU blocks are used on the inner and outer side of the wall with a 50 mm-thick polystyrene layer in the middle. The thermal conductivity value for the whole section is calculated as 0.530 W/m2K, which is bit higher, so a further increase in the insulation thickness can reduce the thermal conductivity value of the section. Figure 3 shows the x-section of the external wall and its thermal properties. Moreover, in partition walls, again, 150-mm CMU blocks are used with plaster on both sides.
In the existing roof section, a 300 mm-thick ribbed concrete slab is used as the structural member, and above it, cement screed is provided for sloping purposes. The bitumen layer is there above the concrete layer for water proofing. Fifty millimeter-thick polystyrene is used as insulation, which might be less, as 70% of the heat is absorbed by the roof, so this may be the most critical area that needs more attention. Above the insulation layer, again, the water-proofing membrane is provided with the cement tile on top. The thermal conductivity value, calculated for the whole section, is 0.490 W/m2K, which is again high. Figure 4 shows the roof x-section and its thermal properties.
In windows, low-e double glazing is used with an aluminum frame, which has a U-value of 2.71 W/m2K. Figure 5 shows the window glass section and its thermal properties.
Since ceiling section does not influence thermal calculations, no thermal insulation layer is provided in the ceiling section. Gypsum board is placed as a false ceiling with a 600-mm air gap to provide air-conditioning ducts. Figure 6 shows the ceiling section and its properties.
In the floor section, a plain cement concrete (PCC) layer is provided with ceramic tiles on the top. PCC is placed on a layer of gravel, while below the gravel, compacted earth is provided. The U-value of the section is 0.47 W/m2K. Figure 7 shows the floor x-section and its thermal properties.
In the proposed green roof section, we are assuming to provide the extensive green roof not only taking into consideration the load-bearing capacity of the existing structure, but also due to the maintenance factor of the green roof. It is also important to mention that a shallow soil depth may result in plants’ root damage from heat and temperature fluctuation, and 2 3/4” soil substrate is suggested by some of the green roof companies for the extensive green roof; but, still it is recommended to provide minimum a 3” deep soil layer. For green roof provision, we are considering green roof layers on existing conventional roofs, where reinforced cement concrete (RCC slab) is used as the main structural member and above which bitumen is provided as the water-proofing membrane. The same 50 mm-thick insulation “extruded polystyrene” layer is considered above the bitumen, which is provided in the existing roof structure, so the true effect of the green roof could be observed. The root barrier with the water proofing membrane is provided above the insulation layer to protect the insulation and the other structure from any damage. The water drainage system, which not only stores rainwater, but also takes excessive water to the gutter, is provided above the root barrier layer. The drainage system is basically recycled plastic modular elements, normally having a 6-cm height. Above the drainage layer, a 150 mm-thick soil bed is placed, and we are considering 150 mm as the plant height above the soil layer. While creating the green roof section on the software ECOTECT, we are considering a 300 mm-thick layer for soil and plants, as plants are not available as material on the software, and the green roof main section (soil layer and plants) works as thermal mass or as shading on the existing roof structure, so considering one thick layer can resolve the problem. The thermal conductivity value calculated for this green roof section is 0.190 W/m2K since we did not change the thickness of the insulation, as used in the conventional roof section. The thermal conductivity value of the green roof section can be further improved by changing the specification and thicknesses of insulation, soil layer and plants. Figure 8 shows the x-section of the proposed green roof and its properties. Since we are considering the extensive green roof on the existing structure, we planned to use a combination of forbs, sedum and grasses, which has better survivability in a hot climate, like Saudi Arabia, as discussed in the literature review [33].

6. Thermal Analysis

All analyses are made on the software ECOTECT. ECOTECT by Autodesk is a unique building performance analysis software that performs a variety of analyses with simple and intuitive 3D modeling. It is user-friendly interface, and compatibility with other software like AutoCAD, REVIT, etc., makes it popular among designers to use from the conceptual to the design stage. It can perform analysis like solar stereographic shadows, overshadowing and solar reflection, sun penetration and shading, analysis of artificial lighting, solar access and photovoltaic/heat collection, acoustic reflections and reverberation times and hourly thermal comfort and monthly space loads with a weather tool option for a specific location [37]. Especially, “solar access analysis” to calculate the incident solar radiation and the “shading design wizard” to design the proper shading make it prominent among other software. Difficulty in creating complex geometry and lacking study of the fluid dynamics are some limitations that this software has.
Heating and cooling loads are a measure of energy needs to be added or removed from a space by either mechanical or natural systems to provide the desired level of comfort within a space [38]. Heating and cooling loads help in choosing the type of system and its capacity. This also helps in choosing duct sizes and its type. These loads have a direct impact on the construction and operational cost, occupant comfort and building durability. To do these analyses, we prepared two separate models with the same materials on the walls, floors, ceiling, windows and doors, as shown in Figure 9. On one model, the conventional roof material was applied, while on the other, the green roof was considered. Monthly load discomfort analysis was run after making the zone settings. The weather data file for Dhahran’s climate is not available in ECOTECT, so we are considering the Kuwait coastal area climate for analysis, since many other software products do the same by default.
The main considerations while making the analysis, as also shown in Figure 10, were:
  • Design for the full air-conditioning system due to the hot weather of Saudi Arabia, where air-conditioning is required twenty four hours a day for 12 months.
  • Thermostat range: 18–26 °C.
  • Operating hours: 24 h/day.
  • Air speed: 0.50 m/s.
  • Clothing factor: 1.0.
  • Air change rate: 0.50.
  • Wind sensitivity: 0.25.

7. Results

Load discomfort analysis informs us about the total energy demand of the building including heating and cooling loads. Monthly load discomfort analysis is made for Dhahran region while considering the Kuwait coastal area weather data file, as the Dhahran weather data file is not available in ECOTECT. It is also important to mention that we are considering detached housing to understand the reduction in energy demand because of the building orientation; otherwise, these houses are placed in different orientations and the proper urban arrangement, as discussed in the project brief. The selected detached building is analyzed with four different orientations, east facing, west facing, north facing and south facing. Initially, analysis is made with the existing roof structure to understand the orientation, consuming the maximum amount of energy. Figure 11, shows the results generated by the software with east- and north-facing models and with the conventional (existing) roof. These results are summarized in Table 1 and Figure 12.
The difference in energy demand for the four orientations is minor with the east-facing one consuming the minimum, 140.3 KWh/m2Y as shown in Table 1. West-facing and north-south-facing orientations respectively consume 140.6 KWh/m2Y and 141.6 KWh/m2Y. It can be concluded that the east-west orientation is consuming less compared to the other three because the longitudinal axis of the building is facing north-south, and since the north side is least exposed to sun and the one of a longer elevation is mostly under shade, so mainly the heat transmission is from the south side only. It also depends on the number of windows provided at different elevations. Furthermore, even if we are going to consider the same orientation with the neighborhood, the results would be even better as now, the southern side of the building will also be under shade because of the adjacent building. On the other hand, the building facing south or north is consuming the maximum amount of energy since the longitudinal axis is facing east-west, and this will be exposed to sun either in the morning or in the afternoon; but the front elevation along the south is exposed to sun most of time, as this time north, which is least exposed to sun, is along the shorter axis, so total energy demand is higher.
The monthly load discomfort analysis in four different orientations with conventional (existing roof) roofs are repeated in the Riyadh climate, and almost a similar type of trend is observed, as shown in Table 2 & Figure 13. The east-west-oriented building is consuming a lesser amount of energy, but the north-facing building has the maximum energy demand. It is also important to mention that in this case study, if the building is north oriented, then the south elevation, which will be the rear in that case, has more windows, which increases the energy demand; that is why the north-facing building has slightly higher energy demand as compared to the south-facing building.
If we are going to compare the total energy demand in two different climates, which are Dhahran and Riyadh, with the existing conventional roof, then the result generated by the software clearly tells that the total energy demand in Riyadh would be almost 14% higher along different orientations, as shown in Table 3. If we are going to compare heating loads in both climates, it is quite clear that these are high in Dhahran, and this is because of the winter duration, as this is for a greater time period in Dhahran. The longer winter period in Dhahran reduces the cooling loads, and hence, total energy demand in the Dhahran climate is less than Riyadh.
Now, we replaced the conventional roof with the green roof in Dhahran climate. Table 4 and Figure 14, show the results generated by the software. In this model, the green roof is placed at the top instead of the conventional roof, while all other specifications (for walls, floors, windows, doors etc.) are the same, and a considerable reduction is noted in the cooling load, as it came down from 132 KWh/m2Y to 124 KWh/m2Y, while the reduction in heating demand is less than 1 KWh/m2Y; which was 7.5 KWh/m2Y before, but became almost 6.8 KWh/m2Y.
Comparing the total energy demand between the conventional and green roof in Dhahran, the latter is found to provide 6.5% of savings with respective loads of 140 KWh/m2Y and 131 KWh/m2Y, as shown in Table 5.
Now, the conventional roof (existing) is replaced with the green roof in Riyadh, and the analyses are made in four different orientations. In terms of orientation, the trend of the energy demand is almost same as the green roof in Riyadh, as east-west is the most suitable orientation with the minimum energy demand, while north-south has the maximum energy demand as shown in Figure 15. Cooling loads got reduced almost 10 KWh/m2Y from 158 KWh/m2Y to 148 KWh/m2Y, while the reduction in heating loads is almost ignorable, as reduction is from 4.3 KWH/m2Y to 4.0 KWh/m2Y as shown in Table 6.
Now, we compared the results of conventional roof with green roof in Riyadh and found that with the east-facing building, the saving can be 6.63% as compared to the conventional roof in the Riyadh climate, and it reaches almost 7% for the south-facing building, as shown in Table 7.
Comparing the effectiveness of the green roof in the hot and humid (Dhahran climate) and the hot and dry climate (Riyadh), we found that the reduction in energy demand is slightly higher in Riyadh as compared to Dhahran, as shown in Table 8, as is also suggested by other studies that the green roof is more effective in a hot and dry climate [18].

8. Discussion

As part of energy conservation strategies in buildings, a number of systems and materials can be applied to reduce the energy demand. Walls, floors, roofs and windows can be designed in such a way that heat losses in winter and heat gain in summer could be minimized. Green roofs are a passive strategy, which insulate the building rooftop. The vegetation component of the green roof reduces the heat gain by working as an active dynamic air envelope system. It provides exterior shading to control the direct solar radiation, thus leading to considerable energy saving. In this research project, we have considered newly-constructed villas in KFUPM, Dhahran Saudi Arabia, as the case study and modelled green roof layers above the existing roof structure with the same insulation thickness as provided in the conventional roof. We considered the extensive green roof for this purpose because of its low maintenance factor and its structural lightness in terms of weight.
To attain our goals, firstly, we prepared two separate models in the software ECOTECT, one with the conventional and the other with the green roof. We placed the conventional roof model in four different orientations facing east, west, north and south and calculated the total energy demand with the Dhahran climate. Then, we replaced the existing conventional roof with the green roof and observed the energy savings. We considered the same building in the Riyadh climate and repeated all analyses to understand the validity of the green roof in two different Saudi climates. Moreover, to understand the energy savings due to the appropriate orientation, we considered the detached residential building. It is also important to mention that the effectiveness of the green roof also depends on the level of insulation provided for the building envelope and windows along with climatic conditions and building function. We analyzed this building with single and double glazing although single glazing results are not included in this research paper but after providing the efficient glazing and better insulated walls, energy saving because of green rooftop became more significant.
With energy savings, the initial cost, maintenance cost and the system’s payback period also need to be considered. Normally, a green roof costs more than most conventional roofs or cool rooftops. Green roofs cost depends on its type (intensive or extensive) and its components’ specifications, like depth of growing medium, type of roofing system, type of drainage system, type of plants, etc. The cost of the extensive and intensive green roof options has been reported to be $10/ft2 and $25/ft2, respectively [39]. Maintenance expenses of the green roof also need to be considered at the time of construction, as it mainly depends on the type of plants provided on it. Most of the maintenance cost emerges in the first year as plants develop, and it can be $0.75–$1.50 for every square foot [40].
Besides energy savings, there are several other benefits that can be attained due to the provision of the green roof. It can also potentially enhance the property value. Although no such data are available showing the increment in property value due to the green roof, according to some statistics, a normal house price can increase by up to 7.1% with close proximity to greenery [41]. It is also important to mention that the life span of the conventional roof is around 20 years, while for the green rooftop, it is 40–55 years [42]. The green rooftop also helps with carbon reduction and controlling air contamination. Dust, particulates and nitrates (NO2) are the measure of the air quality, and different plants have different oxygen-carbon dioxide conversion rates; but, according to a study, 80–85 kg of toxins per hectare per year can be removed by green roofs [43]. In urban areas, the creation of natural surroundings is not a typical interest, and the green roof can help with creating such an environment by providing plants and soil contributing to the richness of the natural habitat. The green roof also helps with mitigating the urban heat island effect. Urban areas are full of dull surfaces with low albedo, which is basically the reflection capability of any surface [44]. Dull surfaces and the absence of vegetation increase the urban air temperature amid summer months [45]. This results in increased building energy demand and consequently more usage of HVAC systems.
The findings of this work reveal that buildings in Saudi Arabia oriented along east-west consume the least amount of energy. It is also reported that the total energy demand of buildings is least when the orientation angle is zero, which means placing the long axis of the building along east-west can be the most suitable option [46]. Similarly, according to Ghobadian (2006), the most suitable orientation in Iran is also east-west, as the length of the building should be towards the south, so in winter, it could gain the maximum solar energy, and in summer, shading devices can be used to protect it from heat [47].

9. Conclusions

The presented work has investigated the impact of the orientation and green roof on the energy performance of buildings in the hot-humid and hot-dry climatic conditions of Saudi Arabia. Dhahran and Riyadh have been used as the representative cities for these two climatic conditions, respectively. The findings of the modeling work undertaken with the help of ECOTECT software reveal a nominal difference in the energy performance of the selected building with varying orientations. For example, in the case of Dhahran, the building consumes 140.3, 140.6, 141.6 and 141.3 KWh/m2Y, respectively, for east, west, north and south facing. The total energy demand in the Riyadh climate is however found to be almost 14% higher than in the Dhahran climate, mainly due to the longer and more intense summer in the case of the former. The green roof is observed to be marginally more effective in the hot and dry climate of Riyadh compared to the hot and humid conditions of Dhahran. The results of the analysis indicate that in the climatic conditions of Dhahran and Riyadh, the green roof can reduce the energy consumption by 6.7% and 6.8%, respectively.

Acknowledgments

The authors would like to acknowledge the support of Deanship of Scientific Research (DSR), King Fahd University of Petroleum and Minerals, Saudi Arabia, who sponsored us to carry out this research project (Reference No. IN141034). Their support allowed us to conduct all modelling and experimental work.

Author Contributions

Hassan Saeed Khan conceived the research idea and did the modeling. Muhammad Asif and Hassan Saeed Khan jointly analyzed the results and wrote the paper.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Asif, M. Growth and Sustainability Trends in the GCC countries with Particular Reference to KSA and UAE. Renew. Sustain. Energy Rev. 2016, 55, 1267–1273. [Google Scholar] [CrossRef]
  2. Alrashed, F.; Asif, M. Climatic Classification of Saudi Arabia for Building Energy Modelling. Energy Procedia 2015, 75, 1425–1430. [Google Scholar] [CrossRef]
  3. Asif, M. Energy Crisis in Pakistan: Origins, Challenges and Sustainable Solutions; Oxford University Press: Oxford, UK, 2011. [Google Scholar]
  4. Alrashed, F.; Asif, M. Trends in Residential Energy Consumption in Saudi Arabia with Particular Reference to the Eastern Province. J. Sustain. Dev. Energy Water Environ. Syst. 2014, 2, 376–387. [Google Scholar] [CrossRef]
  5. Alnaser, W.; Flanagan, R. Model for calculating the sustainable building index (SBI) in the kingdom of Bahrain. Energy Build 2008, 40, 2037–2043. [Google Scholar] [CrossRef]
  6. Paris Agreement. Available online: http://www.cop21.gouv.fr/en/195-countries-adopt-the-first-universal-climate-agreement/ (accessed on 1 January 2017).
  7. Nereim, V.; Mahdi, W.; Fattah, Z. Saudi Arabia to Cut Public Sector Wage Bill in Post-Oil Plan. Available online: http://gulfnews.com/business/economy/saudi-arabia-to-cut-public-sector-wage-bill-in-post-oil-plan-1.1841887 (accessed on 28 March 2017).
  8. Mahmoud, A.S.; Asif, M.; Hassanain, M.A.; Babsail, M.O.; Sanni-Anibire, M.O. Energy and Economic Evaluation of Green Roofs for Residential Buildings in Hot-Humid Climates. Buildings 2017, 7, 30. [Google Scholar] [CrossRef]
  9. D’Souza, U. The thermal performance of green roofs in a hot, humid microclimate. IWIT Trans. Ecol. Environ. 2013, 173, 475–486. [Google Scholar]
  10. Bates, A.J.; Sadler, J.P.; Mackay, R. Vegetation development over four years on two green roofs in the UK. Urban For. Urban Green. 2013, 12, 98–108. [Google Scholar] [CrossRef]
  11. Carter, T.; Butler, C. Cities and the Environment Ecological impacts of replacing traditional roofs with green roofs in two urban areas. Cities Environ. 2008, 1, 1–17. [Google Scholar] [CrossRef]
  12. Ahmadi, H.; Arabi, R.; Fatahi, L. Thermal Behavior of Green Roofs in Different Climates. Curr. World Environ. 2015, 10, 908–917. [Google Scholar] [CrossRef]
  13. Manfred Kohler, M.; Marco Schmidt, M.; Vera Lucia de, A.P.; Taveres, S. Green Roofs in temperate climates and in the hot-humid tropics—Far beyond the aesthetics. Environ. Manag. Health 2002, 4, 382–391. [Google Scholar] [CrossRef]
  14. Teemusk, A.; Mander, U. Temperature rigime of planted roofs compared with convention roofing systems. Ecolo. Eng. 2010, 36, 91–95. [Google Scholar] [CrossRef]
  15. Chow, M.F.; Bakar, M.F. A Review on the Development and Challenges of Green Roof Systems in Malaysia. Int. J. Civ. Environ. Struct. Constr. Archit. Eng. 2016, 10, 16–20. [Google Scholar]
  16. Cutlip, J. Green Roofs: A Sustainable Technology. Sustainability and the Built Environment UC Davis Extension. 2006. Available online: https://extension.ucdavis.edu/sites/default/files/green_roof.pdf (accessed on 28 March 2017).
  17. Syed, A.T.; Abdou, A.A. A Model of a Near-Zero Energy Home (nZEH) using Passive Design Strategies and PV Technology in Hot Climates. J. Green Build. 2016, 11, 38–70. [Google Scholar] [CrossRef]
  18. Erica, O.; Lundholm, J.; Bass, B.; Coffman, R.R.; Doshi, H.; Dunnett, N.; Gaffin, S.; Köhler, M.; Liu, K.K.Y.; Rowe, B. Green roofs as urban ecosystems: Ecological structures, functions, and services. BioScience 2007, 10, 823–833. [Google Scholar]
  19. Muharam, A.; Amer, E.; Al-Hemiddi, N. Thermal Performance of the Extensive Green Roofs in Hot Dry Climate. Int. J. Adv. Eng. Res. Sci. (IJAERS) 2016, 3, 2349–6495. [Google Scholar]
  20. Gago, E.; Roldan, J.; Pacheco-Torres, R.; Ordonez, J. The city and urban heat islands: A review of strategies to mitigate adverse effects. Renew. Sustain. Energy Rev. 2013, 25, 749–758. [Google Scholar] [CrossRef]
  21. Goussous, J.; Siam, H.; Alzoubi, H. Prospect of green roof technology for energy and thermal benefits in buildings: Case study of Jordan. Sustain. Cities Soc. 2014, 192, 1–16. [Google Scholar] [CrossRef]
  22. Fioretti, R.; Palla, A.; Lanza, L.G.; Principi, P. Green roof energy and water related performance in the Mediterranean climate. Build. Environ. 2010, 8, 1890–1904. [Google Scholar] [CrossRef]
  23. Qin, X.; Wu, X.; Chiew, Y.-M.; Li, Y. A Green Roof Test Bed for Stormwater Management and Reduction of Urban Heat Island Effect in Singapore. Br. J. Environ. Clim. Chang. 2012, 2, 410–420. [Google Scholar] [CrossRef] [PubMed]
  24. Zhang, L.; Zhang, R.; Zhang, Y.; Hong, T.; Menga, Q.; Fenga, Y. The impact of evaporation from porous tile on roof thermal performance: A case study of Guangzhou’s climatic conditions. Energy Build. 2017, 136, 161–172. [Google Scholar] [CrossRef]
  25. Schweitzer, O.; Erell, E. Evaluation of the energy performance and irrigation requirements of extensive green roofs in a water-scarce Mediterranean climate. Energy Build. J. 2014, 68, 25–32. [Google Scholar] [CrossRef]
  26. Ouldboukhitine, S.; Belarbi, R.; Djedjig, R. Characterization of green roof components: Measurements of thermal and hydrological properties. Build. Environ. J. 2012, 56, 78–85. [Google Scholar] [CrossRef]
  27. Wong, N.H.; Cheong, D.W.K.; Yan, H.; Soh, J.; Ong, C.L.; Sia, A. The effects of rooftop garden on energy consumption of a commercial building in Singapore. Energy Build. 2003, 4, 353–364. [Google Scholar] [CrossRef]
  28. Jim, C.Y.; Peng, L.L.H. Substrate moisture effect on water balance and thermal regime of a tropical extensive green roof. Ecol. Eng. J. 2012, 47, 9–23. [Google Scholar]
  29. Nagase, A.; Dunnett, N. The relationship between percentage of organic matter in substrate and plant growth in extensive green roofs. Landsc. Urban Plann. J. 2011, 103, 230–236. [Google Scholar]
  30. Sheweka, S. M.; Magdy, N. The Impact of Different Green Roofs Strategies on the Indoor Thermal Comfort with Special Reference to Cairo-Egypt. Adv. Mater. Res. 2014, 935, 38–43. [Google Scholar] [CrossRef]
  31. Fabricio, B.; Hewage, K. How “green” are the green roofs? Lifecycle analysis of green roof materials. Eng. Appl. Sci. 2012, 57–65. [Google Scholar]
  32. Farrell, C.; Mitchell, R.E.; Szota, C.; Rayner, J.P.; Williams, N.S.G. Green roofs for hot and dry climates: Interacting effects of plant water use, succulence and substrate. Ecol. Eng. 2012, 49, 270–276. [Google Scholar] [CrossRef]
  33. Ayako, N.; Dunnett, N. Drought tolerance in different vegetation types for extensive green roofs: Effects of watering and diversity. Lands. Urban Plan. 2010, 97, 318–327. [Google Scholar]
  34. Report on Saudi Climate. Available online: http://www.weatheronline.co.uk/reports/climate/Saudi-Arabia.htm (accessed on 28 March 2017).
  35. Average Weather for Dhahran, Saudi Arabia. Available online: https://weatherspark.com/averages/32761/Dhahran-Eastern-Province-Saudi-Arabia (accessed on 28 March 2017).
  36. Average Weather for Riyadh, Saudi Arabia. Available online: https://weatherspark.com/averages/32777/Riyadh-Saudi-Arabia (accessed on 28 March 2017).
  37. Andrew, R.; Andrew, M. ECOTECT: Environmental Prediction in Architectural Education; Cardiff University: Wales, UK, 2001. [Google Scholar]
  38. US Department of Energy. Strategy Guideline Accurate Heating and Cooling Load Calculations, Energy Efficiency & Renewable energy; US Department of Energy: Washington, DC, USA, 2011.
  39. Report on Reducing Urban Heat Islands: Compendium of Strategies Green Roofs; United States Environmental Protection Agency: Washington, DC, USA, 2014.
  40. Yang, R. Report on a Living Campus, Assessing the Viability for Green Roofs and Walls on the Williams College Campus. Available online: https://sustainability.williams.edu/files/2015/04/Yang_A-Living-Campus.pdf (accessed on 28 March 2017).
  41. Benefits of Green Infrastructure. Available online: https://www.epa.gov/green-infrastructure/benefits-green-infrastructure (accessed on 28 March 2017).
  42. Corrie, C.; Adriaens, P.; Talbot, F.B. Green roof valuation: A probabilistic economic analysis of environmental benefits. Environ. Sci. Technol. 2008, 42, 2155–2161. [Google Scholar]
  43. Yang, J.; Qian, Y.; Peng, G. Quantifying air pollution removal by green roofs in Chicago. Atmos. Environ. 2008, 42, 7266–7273. [Google Scholar] [CrossRef]
  44. Susca, T.; Gaffin, S.R.; Dell’Osso, G.R. Positive effects of vegetation: Urban heat island and green roofs. Environ. Pollut. 2011, 159, 2119–2126. [Google Scholar] [CrossRef] [PubMed]
  45. Kum, D.M.; Bretz, S.E.; enson Huang, B.; Akbari, H. The Potential for Reducing Urban Air Temperatures and Energy Consumption through Vegetative Cooling; Heat Island Project Energy and Environment Division, Lawrence Berkeley Laboratory: Berkeley, CA, USA, 1994.
  46. Muhaisen, A.S.; Dabboor, H.R. Studying the Impact of Orientation, Size, and Glass Material of Windows on Heating and Cooling Energy Demand of the Gaza Strip Buildings. J. Archit. Plan. 2013, 27, 1–15. [Google Scholar]
  47. Fallahtafti, R.; Mahdavinejad, M. Optimisation of building shape and orientation for better energy efficient architecture. Int. J. Energy Sect. Manag. 2015, 9, 593–618. [Google Scholar] [CrossRef]
Figure 1. Compound consisting of 200 new villas inside KFUPM.
Figure 1. Compound consisting of 200 new villas inside KFUPM.
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Figure 2. (a) Ground Floor plan of KFUPM faculty housing; (b) first Floor plan of KFUPM faculty housing.
Figure 2. (a) Ground Floor plan of KFUPM faculty housing; (b) first Floor plan of KFUPM faculty housing.
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Figure 3. External wall x-section and its properties. CMU, concrete masonry units.
Figure 3. External wall x-section and its properties. CMU, concrete masonry units.
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Figure 4. Existing roof x-section and its properties.
Figure 4. Existing roof x-section and its properties.
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Figure 5. Double-glazed window section and its properties.
Figure 5. Double-glazed window section and its properties.
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Figure 6. Ceiling section and its properties.
Figure 6. Ceiling section and its properties.
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Figure 7. Ground floor section and its properties.
Figure 7. Ground floor section and its properties.
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Figure 8. Proposed green roof section and its properties.
Figure 8. Proposed green roof section and its properties.
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Figure 9. Models of faculty housing: (a) with conventional roof; (b) with green roof.
Figure 9. Models of faculty housing: (a) with conventional roof; (b) with green roof.
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Figure 10. Zone setting for both models.
Figure 10. Zone setting for both models.
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Figure 11. Monthly Load discomfort analysis in Dhahran with the conventional roof.
Figure 11. Monthly Load discomfort analysis in Dhahran with the conventional roof.
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Figure 12. Total energy demand comparison with four different orientations and the conventional roof in Dhahran.
Figure 12. Total energy demand comparison with four different orientations and the conventional roof in Dhahran.
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Figure 13. Total energy demand comparison with four different orientations and the conventional roof in Riyadh.
Figure 13. Total energy demand comparison with four different orientations and the conventional roof in Riyadh.
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Figure 14. Total energy demand comparison with four different orientations and the green roof in Dhahran.
Figure 14. Total energy demand comparison with four different orientations and the green roof in Dhahran.
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Figure 15. Total energy demand comparison with four different orientations and the green roof in Riyadh.
Figure 15. Total energy demand comparison with four different orientations and the green roof in Riyadh.
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Table 1. Total Energy demand comparison with four different orientations and the conventional roof in Dhahran.
Table 1. Total Energy demand comparison with four different orientations and the conventional roof in Dhahran.
Conventional Roof in Dhahran, Total Energy Demand Comparison (Monthly Load Discomfort Analysis) with Different Orientation
OrientationHeating Load (KWh/m2Y)Cooling Load (KWh/m2Y)Total Energy Demand (KWh/m2Y)
East facing7.4132.9140.3
North Facing7.5134.1141.6
West facing7.3133.3140.6
South facing7.3134.0141.3
Table 2. Total energy demand comparison with four different orientations and the conventional roof in Riyadh.
Table 2. Total energy demand comparison with four different orientations and the conventional roof in Riyadh.
Conventional Roof in Riyadh, Total Energy Demand Comparison (Monthly Load Discomfort Analysis) with Different Orientation
OrientationHeating Load (KWh/m2Y)Cooling Load (KWh/m2Y)Total Energy Demand (KWh/m2Y)
East facing4.3158.2162.5
North Facing4.4159.7164.1
West facing4.3158.6162.8
South facing4.2159.6163.8
Table 3. Total energy demand comparison in Dhahran and Riyadh with the conventional roof.
Table 3. Total energy demand comparison in Dhahran and Riyadh with the conventional roof.
Conventional Roof Comparison in Dhahran and Riyadh, Total Energy Demand (Monthly Load Discomfort Analysis) with Different Orientation
OrientationTotal Energy Demand in Dhahran with Conventional Roof (KWh/m2Y)Total Energy Demand in Riyadh with Conventional Roof (KWh/m2Y)Difference in Total Energy Demand (KWh/m2Y)Difference in %
East facing140.3162.522.213.67
North Facing141.6164.122.513.72
West facing140.6162.822.213.65
South facing141.3163.822.513.73
Table 4. Total energy demand comparison with four different orientations and the green roof in Dhahran.
Table 4. Total energy demand comparison with four different orientations and the green roof in Dhahran.
Green Roof in Dhahran, Total Energy Demand Comparison (Monthly Load Discomfort Analysis) with Different Orientation
OrientationHeating Load (KWh/m2Y)Cooling Load (KWh/m2Y)Total Energy Demand (KWh/m2Y)
East facing6.8124.3131.1
North Facing6.9125.1132.0
West facing6.8124.7131.5
South facing6.7125.0131.7
Table 5. Total energy demand comparison in Dhahran with the conventional roof and the green roof.
Table 5. Total energy demand comparison in Dhahran with the conventional roof and the green roof.
Conventional vs. Green Roof in Dhahran, Total Energy Demand (Monthly Load Discomfort Analysis) Comparison with Different Orientation
OrientationTotal Energy Demand in Dhahran with Conventional Roof (KWh/m2Y)Total Energy Demand in Dhahran with Green Roof (KWh/m2Y)Reduction in Energy Demand (KWh/m2Y)Saving in %
East facing140.3131.19.26.55
North Facing141.6132.09.66.76
West facing140.6131.59.16.50
South facing141.3131.79.76.83
Table 6. Total energy demand comparison with four different orientations and the green roof in Riyadh.
Table 6. Total energy demand comparison with four different orientations and the green roof in Riyadh.
Green Roof in Riyadh, Total Energy Demand Comparison (Monthly Load Discomfort Analysis) with Different Orientation
OrientationHeating Load (KWh/m2Y)Cooling Load (KWh/m2Y)Total Energy Demand (KWh/m2Y)
East facing4.0147.8151.7
North Facing4.1148.7152.8
West facing3.9148.1152.1
South facing3.9148.5152.4
Table 7. Total energy demand comparison in Riyadh with the conventional roof and the green roof.
Table 7. Total energy demand comparison in Riyadh with the conventional roof and the green roof.
Conventional vs. Green Roof in Riyadh, Total Energy Demand (Monthly Load Discomfort Analysis) Comparison with Different Orientation
OrientationTotal Energy Demand in Riyadh with Conventional Roof (KWh/m2Y)Total Energy Demand in Riyadh with Green Roof (KWh/m2Y)Reduction in Energy Demand (KWh/m2Y)Saving in %
East facing162.5151.710.86.63
North Facing164.1152.811.36.89
West facing162.8152.110.86.61
South facing163.8152.411.46.96
Table 8. Green roof saving comparison in Riyadh and Dhahran.
Table 8. Green roof saving comparison in Riyadh and Dhahran.
Green Roof Saving Comparison in Dhahran and Riyadh
OrientationSaving in % due to Green Roof in RiyadhSaving in % due to Green Roof in DhahranDifference
East facing6.636.550.08
North Facing6.896.760.13
West facing6.616.500.11
South facing6.966.830.13

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Khan, H.S.; Asif, M. Impact of Green Roof and Orientation on the Energy Performance of Buildings: A Case Study from Saudi Arabia. Sustainability 2017, 9, 640. https://doi.org/10.3390/su9040640

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Khan HS, Asif M. Impact of Green Roof and Orientation on the Energy Performance of Buildings: A Case Study from Saudi Arabia. Sustainability. 2017; 9(4):640. https://doi.org/10.3390/su9040640

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Khan, Hassan Saeed, and Muhammad Asif. 2017. "Impact of Green Roof and Orientation on the Energy Performance of Buildings: A Case Study from Saudi Arabia" Sustainability 9, no. 4: 640. https://doi.org/10.3390/su9040640

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