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Article

Renewable Energy Potential by the Application of a Building Integrated Photovoltaic and Wind Turbine System in Global Urban Areas

1
Illinois School of Architecture, University of Illinois at Urbana-Champaign, Champaign, IL 61820, USA
2
Department of Civil and Environmental Engineering, KAIST, Daejeon 305-701, Korea
3
Department of Architecture, Inha University, Inharo 100, Nam-gu, Incheon 402-751, Korea
*
Authors to whom correspondence should be addressed.
Energies 2017, 10(12), 2158; https://doi.org/10.3390/en10122158
Submission received: 25 November 2017 / Revised: 25 November 2017 / Accepted: 13 December 2017 / Published: 17 December 2017

Abstract

:
Globally, maintaining equilibrium between energy supply and demand is critical in urban areas facing increasing energy consumption and high-speed economic development. As an alternative, the large-scale application of renewable energy, such as solar and wind power, might be a long-term solution in an urban context. This study assessed the overall utilization potential of a building-integrated photovoltaic and wind turbine (BIPvWt) system, which can be applied to a building skin in global urban areas. The first step of this study was to reorganize the large volume of global annual climate data. The data were analyzed by computational fluid dynamic analysis and an energy simulation applicable to the BIPvWt system, which can generate a Pmax 300 Wp/module with a 15% conversion efficiency from a photovoltaic (PV) system and a 0.149 power coefficient/module from wind turbines in categorized urban contexts and office buildings in specific cities; it was constructed to evaluate and optimize the ratio that can cover the current energy consumption. A diagram of the distribution of the solar and wind energy potential and design guidelines for a building skin were developed. The perspective of balancing the increasing energy consumption using renewable energy in urban areas can be visualized positively in the near future.

1. Introduction

The need and flow of energy in urban areas has increased rapidly. Currently, approximately 3.2 billion people live in urban areas and the urban population is expected to increase to approximately 5 billion by 2030 [1]. Among those cities, most areas show large and small issues related to environmental and energy problems [2]. Buildings are responsible for 30–40% of all primary energy and 40–50% of greenhouse gas emitted [3]. Therefore, the increasing energy concerns to maintain the balance between energy supply and demand are being managed using several methods: optimization of energy consumption, design guidelines and strategies, and application of renewable energy.
Energy use in the building sector can be optimized using a range of technological developments and skills. The energy used in buildings is composed mainly of heating, cooling, and lighting. In regions where heating is dominant, especially in northern Europe, the proportion accounts for approximately 70% of the total energy, and in regions where cooling is dominant, the cooling load accounts for more than 70% of the total [4,5,6]. Of course, lighting comprises a considerable portion of the office building, which ranges from approximately 15% to 50%. These values may vary in proportion or absolute value according to changes in the input parameters, such as the building type, orientation, and heating, ventilation, and air-conditioning (HVAC) schedule [7]. Several optimization simulation programs and theories, such as a genetic algorithm, have been applied to urban areas and buildings through optimization [8,9,10,11,12]. As a maintenance phase, advanced control system methods have been introduced for energy and occupant comfort [13]. In addition to the building form and control technique, optimization of the components of a building skin have been introduced, which also works effectively as energy management [14,15,16,17].
Second, the approach by presenting strategies, such as design guideline work, effectively improves the building aesthetics and reduces the energy consumption in buildings and urban areas [18]. Some related studies examined how urban and building design can work effectively under certain climate conditions. Therefore, thermal comfort analysis was performed in certain climates and the strategy-related form, orientation, and spatial layout essential to the proper performance were handled [19,20,21]. As another guideline, solar and lighting design technologies were evaluated in terms of their effects on energy, environment, and health [22,23,24].
In addition, although architects and engineers can reduce their energy consumption through optimization and design, buildings and urban areas are some of the main sources of energy expenditure, which inevitably require the application of renewable energy for urban sustainability. As the main applicable source in building and urban areas, researchers have mainly examined photovoltaics (PV), wind, bio, and geothermal energy [25,26]. The economic value and financial analysis of those energy sources was performed and their technological competitiveness is increasing [27]. In addition, studies related to building-integrated renewable energy systems, such as PV thermal systems and window-integrated transparent PV systems, have been performed [28,29]. As an application of renewable energy, studies involving solar radiation analysis, the PV tracking system, and increasing wind turbine performance have been conducted [30,31,32], and the visual impact of building integrated photovoltaics (BIPV) [33] and the application of BIPV on a wall system [34] have been investigated. In addition, as a hybrid system, the prospect of an integrated PV and wind turbine system was studied [35,36,37]. Several studies have examined a range of solar and wind power systems, e.g., sun tracking PV and wind hybrid systems [38], the optimal size of the PV and wind hybrid system [39], and the validity of PV and wind energy harvesting in double skins [40,41,42]. Hence, the main topic of the current study was to increase the efficiency of PV or wind power, improve their applicability and feasibility, or apply large-scale hybrid systems. Accordingly, it is necessary to develop and analyze a hybrid system that is applicable on a small scale, particularly a building facade.
In this paper, the solar and wind energy potential in urban areas was estimated by applying buildings with an integrated PV and wind turbine (BIPvWt) system. The proposed BIPvWt system has an advantage in attaching to a building skin to generate sustainable and clean energy, and it was initially introduced as a building-integrated wind turbine (BIWt) system [43]. The integration of a micro wind turbine with the ventilated building skin for energy harvesting was a fairly new design concept. Based on the basic principle of this system, a more sophisticated device was tested and an evaluation of the renewable energy potential of a building system in global urban areas could be implemented. In addition, the BIPvWt system was introduced and the performance of the energy generation potential in different cities was evaluated as an application of the system to the building area. Eventually, a feasibility study will be performed by simulating and optimizing the application of a BIPvWt system in the perspective of both design and engineering as a contribution towards balancing energy consumption and generation in urban areas.

2. Methods

This section presents the methodology used in this study to determine the renewable energy potential and energy consumption and generation in a specific region. For the input data, several variations, such as climate and the PV and wind turbine properties, were tested.
The analysis procedure was as follows:
  • Introduce a proposed BIPvWt system
  • Classify the climate data in global cities
  • Plot an energy potential chart and diagram by the variation of solar irradiation and wind power
  • Set the building module and BIPvWt system for energy generation and consumption output
  • Analyze the energy balance as an application of the BIPvWt in specific areas in terms of energy consumption and generation.

2.1. Climate Data

The climate data was selected from the American Society of Heating, Refrigerating, and Air-Conditioning Engineers (ASHRAE) and Energy Efficiency & Renewable Energy (EERE), which have information on more than 2100 city locations [44]. The paper selects 143 representative cities as variables to compare the solar and wind energy potential in the ASHRAE climate data. They are the major cities in Europe and Asia, and in each state of the U.S. Some cities are capitals of each country or state, and the others are selected based on the population and population density. In addition, the U.S. has the most cases compared to other areas because the climate data is well distributed in terms of climate classification and the weather data is relatively convincing. Each zone was classified according to the ASHRAE standard, which ranges from zone 1 (very hot) to 8 (subarctic), and the zone was analyzed using the thermal and humidity criteria. The population and density data in selected cities were well defined and informed (Demographia 2015). Figure 1 presents a histogram of the city lists according to the ASHRAE climate classification.

2.2. Energy Simulation and Input Data

Two simulation programs were used to evaluate the energy potential, BIPvWt: the ESP-r simulation program for an analysis of the PV and building energy consumption, and ANSYS Fluent for a computational fluid dynamics (CFD) analysis of the performance of the wind power conversion system [8,45]. ANSYS Fluent is one of the most-used CFD software offering various turbulence models based on the Reynolds-Averaged Navier Stokes (RANS) model. The power production of the wind turbines is estimated by an examination of the wind speed distribution around the applied system through CFD analyses. The ESP-r software package is recognized and used widely in more than 70 countries as an industry standard for the simulations. The authors employed ESP-r 11.1, which considers the energy use of heating, cooling, lighting, and PV energy generation. Thus, ESP-r has been used extensively to assess building energy applications, particularly as a simulation tool to compare various cities [14,29]. In addition, the energy performance of the PV module has been analyzed based on information, such as the open circuit voltage (Voc), short circuit current (Isc), and maximum power point voltage (Vmpp) in the simulation [46]. The information on the solar PV for the energy simulation is based on the data provided by the manufacturer for a silicon-based PV system [47].
As the input variables, three types of building facade including BIPvWt system and climate change in each city were applied. As the output variables, building energy consumption (heating, cooling, and lighting energy) and generation (PV and wind turbine) were considered. As simulation modeling, the office building was comprised of 4 perimeter zones, 4.57 m (15 ft) in depth and 6.10 m (20 ft) in width, with a floor-to-floor height of 3.05 m (10 ft) [13,48], as shown in Figure 2A. Three different simulation cases were considered: (1) 100% Window Wall Ratio (WWR)—“b1” Basic module; (2) 33% WWR—“b2” Basic module 2; and (3) 33% WWR with BIPvWt system—“BI”, as shown in Figure 2B–D, respectively. The U-factor of the envelopes was set by the ASHRAE standard, 100% WWR was used as the basic module, and 33% WWR was used as the BIPvWt building type. The height of the building used in the simulation was set as the highest skyscraper in this study, which can avoid the local factor of wind disturbance and inference on an urban scale.
Table 1, Table 2 and Table 3 list the other calculation assumptions, such as the infiltration and operation schedules. A 27.9 m2 (300 ft2) space is available for each person in the office building under consideration [28]. Based on this, the internal loads for the equipment were calculated to be 8.07 W/m2 (0.75 W/ft2) peak load. The sensible load per person was 297 W, which is 8.07 W sensible/m2 (0.75 W sensible/ft2). As a lighting control, the calculation data was set with a constant lighting level of 538 lx by continuous dimming [13,29].

2.3. BIPvWt System and Performance Efficiency

Park et al. [43] proposed a BIWT module utilizing a building skin. The BIWT module consisted of a rotor and a guide vane, which is the key composition that changes the approaching wind conditions, such as low velocity or high static pressure, to be appropriate for rotor operation. The proposed BIPvWt system, which is shown in Figure 3A, replaces a part of the guide vane with a silicon based PV. To determine the general form of the wind turbine system, the rotating direction of the rotor and the number and shape of the blades are considered using CFD analyses [43,49,50]. The rotor’s total power coefficient, including generator efficiency, was 0.149 [43]. In addition, a silicon cell PV system installed on the guide vane can generate Pmax 300 Wp/module with a 15% conversion efficiency. As an application, the BIPvWt system covers 30% of the upper bound of the building envelope because the approaching wind speed is faster in that region. The width and height of a unit module were 1.5 m (5 ft) to apply them easily to one perimeter zone.
Using the attached BIPvWt, it might work as a double skin façade. In the inside of the cavity space between the glass and external BIPV, 1.5 m gap, the air is accelerated, which might decrease the cooling load when it is ventilated [51,52]. In addition, the external additional skin provides an insulation effect by increasing the external heat transfer resistance. According to recent field studies [53,54,55], a properly installed double skin façade reduces the building energy load by 10% to 40% of the original energy consumption. Therefore, the proposed BIPvWt system can reduce the energy consumption more than expected, even though the current simulation does not fully support the effects of the double skin façade on the ventilation effect for the cooling load.

2.4. CFD Analyses and Calculation Assumptions for Wind Turbine

Full-scale CFD analyses were conducted to examine the performance of each module installed on the target building. Modelling the entire proposed system including the rotor takes a long time, so only the guide vane part was considered for the simulation. The differential pressure coefficient was calculated by measuring the undisturbed outlet velocity magnitudes of each module. Owing to the symmetric shape of the installed system, the results of the two models, whose wind-approaching angle is θ and −θ, are also symmetric so one of them can replace another. For that reason, three different angles of incidence (0°, 22.5°, and 45°) were considered to reduce the number of analysis cases [56].
The power production of the wind turbines of a BIPvWt system applied to a building envelop was estimated by the annual wind data from selected cities. The wind rose data were fitted using the Weibull distribution, which is a good fit to the measured wind speed data [57], for each wind direction [58,59]. In addition, the applied system was assumed to generate electric power from the approaching wind within an angle of 90°. For example, the system installed in a northward direction is affected by wind from the northeast, north-northeast, north, north-northwest, and northwest azimuths. Finally, the total power production of the applied system installed towards the φ direction can be written as the sum of the power converted from five different approaching wind directions as follows:
Power φ , total = Power φ , 45 ° + Power φ , 22.5 ° + Power φ , 0 ° + Power φ , 22.5 ° + Power φ , 45 °

3. Results and Discussion

The results are divided into two parts: energy potential analysis in multiple urban areas and energy balance evaluation in selected cities. In the first part, as shown in the Appendix A, the energy potential can be compared according to the variation of global cities, which have their own climate patterns. Second, a feasibility test was performed by analyzing the energy consumption and generation in an office module in a specific building.

3.1. Solar and Wind Energy Potential in Urban Area

The solar and wind energy generation potential based on the solar irradiation and wind speed and direction were analyzed. A unit, relative ratio (average value: 1.00), was used to compare the renewable energy potential. The climate data of 142 cities were considered to represent the energy generation in a typical major city. For example, the average value was calculated based on the data from 142 targeted cities among a total 1042 locations, which is provided in the weather data set. A relative ratio of 1 means that the city has an average value of the 142 cities. Therefore, the average level of solar irradiation and wind speed in each city was selected as 1. If the value is greater than 1, there is a high potential for energy generation. Conversely, if the value is less than 1, there is a low potential of energy generation. Initially, the solar and wind energy potentials were compared by the ASHRAE international climate classification to determine the regional similarity and difference in each energy potential. As shown in Figure 4, the solar energy potential showed some analogy in the same climate classification compared to the wind case. These results can be explained by the characteristics of the ASHRAE standard, which originate from the division of the thermal and humidity criteria [44]. In the wind energy cases, however, the variation is dispersed irregularly in a similar climate or adjacent cities.
Based on the energy potential data set, Table 4 and Figure 5 and Figure 6 provide a statistical summary and a diagram of the distribution of the solar and wind energy potential, respectively. In addition, the basic abbreviated terms are the maximum value (Max), minimum value (Min), average value (AVG), and standard deviation (S.D.). In the case of Wellington, New Zealand, its energy potential has a maximum value (total: 2.25, solar: 0.97, and wind: 3.53), which has common characteristics in a wind dominated region (average wind energy potential in Australia is 1.15 and New Zealand is 2.31). On the other hand, in the case of Chongqing located in China, its potential has a minimum value (total: 0.31, solar: 0.47, and wind: 0.15), which can explain the regional features of a basin.
In terms of data analysis based on the solar irradiation and wind speed, cities in the U.S. have a relatively high average (AVG) value than other regions. AVG in U.S. is 1.11, which has a high solar and wind energy potential; cities in Asia and Europe have an AVG value of 0.92 and 0.91, respectively. Cities in Asia are low wind speed cities, which have a 0.81 AVG value in wind energy potential. In cities in Europe, however, the wind energy potential (1.06 AVG value) is dominant compared to the solar energy potential (0.75 AVG value).
From the point of view of deviation, there are differences between the solar and wind energy potential. The standard deviation (S.D.) in solar energy is in the range, 0.17, 0.21, and 0.19, and the wind energy is in the range, 0.46, 0.69, and 0.72, respectively. Those distinctions can explain why the wind direction and speed are much more random and highly erratic compared to the solar case [60].
Among the three exemplary regions, two cities representative of the population and high-energy potential were selected and are marked in Figure 5 and Figure 6. Table 5 lists the potential data for the six cities chosen. The main criteria for cities selection are (1) the relative range of energy potentials are between 0.7 and 1.5, which are lower 15% and upper 15% bound, and (2) large population and high density are the main consideration for future energy demand. In the next part, the detailed energy simulations in specific cities were tested based on the energy potential data source.

3.2. Building Energy Balance Simulation in Specific Office Module in Global Urban Areas

Six cities, which are listed in Table 5, (A) New York City (N.Y.), (B) San Francisco (S.F.), (C) Tokyo-Yokohama (Tokyo), (D) Seoul-Incheon (Seoul), (E) Copenhagen, and (F) Amsterdam, were simulated to compare the energy balance of the building modules. First, in the part of solar and PV, the variation of the angle of incidence and its effects on energy generation were examined. In terms of the exterior design, solar panels installed parallel to the elevation can have an integrated design and a sophisticated feel. On the other hand, the PV angle of incidence can also vary the input wind speed as well as the efficiency of the PV. Figure 7 shows the results of the PV angle and its energy generation. Based on the data from six cities, the optimal angle in the PV output might be in the range of 30 to 45° of the roof side. In addition, the reduction ratio in energy generation at a 90° angle of the roof side compared to the best performance angle (30° of the roof side) appears to be an average of 24.4% (21% to 30%). PV energy production is closely related to the climatic conditions, and it tends to be proportional to the solar irradiance. For example, in the case of an angle of 67.5° from the roof, the PV energy output is approximately 8.24 kWh/(m2·y) (San Francisco), 6.57 kWh/(m2·y) (New York), 5.7 kWh/(m2·y) (Tokyo), 5.42 kWh/(m2·y) (Seoul), 4.68 kWh/(m2·y) (Amsterdam), and 4.29 kWh/(m2·y) (Copenhagen), respectively. This shows that the energy production can vary by up to 1.92 times using the same module within different climate conditions.
Solar irradiation has a decisive influence on PV energy production. Figure 8 shows the yearly energy output of PV by global horizontal irradiance based on an energy simulation of the 90° angle of a roof side PV application. According to the data, the energy outputs have a linear relationship according to the change in solar irradiation, which suggests that comparing the solar energy potential with solar irradiation is an appropriate method.
In the case of the wind related data, Figure 9 shows the generated power output of a wind turbine performed by a wind tunnel test. As the inlet velocity increases, the energy generation of a wind turbine is intensified. Figure 10 presents the yearly energy output of a wind turbine by the wind related climate data, such as speed and direction. According to the graph, to some extent, the energy output has a linear relationship with the change in wind climate data, which suggests that a comparison of the wind energy potential with the wind speed and direction is an appropriate method.
Evaluating the energy consumption and generation output by the application of a BIPvWt system in building envelope differs according to the climate conditions and building design and type. The energy output from the office buildings in the six selected cities was analyzed, as shown in Table 6 and Figure 11. The energy generation by PV and wind power differs according to the orientation that the building is facing. In addition, the energy consumption (heating, cooling, and lighting energy load) are different in terms of orientation and building material. In this evaluation, eight different orientations (South East, SE; South, S; South West, SW; West, W; North West, NW; North, N; North East, NE; and East, E) and three different types of envelopes (b1, Basic module; b2, Basic module2; and BI, BIPvWt module) in the six selected cities (N.Y., S.F., Tokyo, Seoul, Copenhagen, and Amsterdam) were simulated and drawn as a graph. In Figure 11, “+” in the y axis stands for the energy consumption, and “−“ stands for the energy generation.
The experimental results are presented in the following order: total energy consumption, WWR changes, orientation effect, total energy balance with PV, and wind energy generation. Before that, details and a thorough investigation of N.Y. was performed. N.Y. has the largest area, with a population ranked 8th and population density ranked 76th in the 142 target cities. PV and wind energy potential occupy a considerably higher 9th place. Hence, installation of the proposed BIPvWt system will have a considerable influence. Based on the average energy data shown in Figure 11, the cooling, heating, and lighting energy consumption ratios were estimated to be 20%, 55%, and 25%, respectively. When the proposed system is installed, it is expected it will not only reduce the energy consumption by approximately 25% as the WWR is lowered, but also produce energy reserves of up to 32% in terms of 3.8 kWh/(m2·y) in PV and 2.05 kWh/(m2·y) in wind energy generation. On the other hand, this shows a large deviation for each orientation. For example, the north orientation consumes the most energy and the south the least, with a ratio of approximately 1:0.79. In particular, the difference in heating energy consumption in relation to the orientation is significant (approximately 22.4 kWh/(m2·y) in the north orientation, and 3.23 kWh/(m2·y) in the south orientation). The difference in energy consumption according to the orientation requires further consideration in building design and renovation. In addition, the west and southwest are the most efficient in energy production, which can replace approximately 18% and 20% of the building energy consumption, respectively. Overall, significantly different results can be obtained in terms of energy consumption and generation depending on where the office is placed, how the layout is organized, and whether the proposed system is installed.
In the total energy consumption, the portion of the cooling and heating loads in the buildings in S.F., which have relatively small needs, had the lowest energy balance (16.0 kWh/(m2·y)) among the cities tested. On the other hand, the buildings in N.Y. required the highest total energy output (49.7 kWh/(m2·y)) because the N.Y. case consumes considerable energy in cooling and heating. Although 4 cities without S.F. (3C) and Copenhagen (5C) are in a similar climate classification (4A) based on the ASHRAE (Table 5), the absolute total energy consumption, and the fact that the ratio between heating, cooling, and lighting energy vary in each city. In addition, depending on the region, the dominance of heating, cooling, and lighting may be different. Of the data in Figure 11, the ratio of energy usage is compared using the mean value of 100% (b1) and 33% (b2) WWR. For example, cooling is relatively dominant in N.Y. (approximately 56% of the total, up to 75%), lighting is relatively dominant in S.F. (approximately 60% of the total), cooling is slightly dominant in Seoul and Tokyo (approximately 40% and 52% of the total), while heating is dominant in Copenhagen and Amsterdam (approximately 57% and 44% of the total, up to 75%). This can vary depending on the changes in input parameters, such as building type, orientation, and HVAC (heating, ventilation, and air-conditioning) schedule. In particular, the ratio may vary significantly depending on orientation of the same area, indicating that the role of orientation in building design and layout can be considerable.
When the WWR changes from 100% to 33%, all cases showed that both the heating and cooling loads decrease and the lighting load increases. On the other hand, the total energy consumption decreases, because the plus amount of heating and cooling load is far outweighed compared to the minus amount of lighting load. As the WWR decreases from 100% (b1) to 30% (BI), 44.8% of the heating, cooling, and lighting load is decreased in the north of the Copenhagen area and 28% is decreased in the south of S.F. In other regions, a 39% (Amsterdam, northeast), 32.1% (Seoul, north), 28.6% (Tokyo, north), and 35.4% (N.Y., southwest) decrease in energy is observed when the WWR changes. This may be characterized by the interaction between the general climatic conditions (temperature or irradiation) and heating or cooling. In other words, in S.F., where the cooling is dominant, energy losses are reduced greatly in relation to the south, and in Copenhagen and Amsterdam, where the heating is dominant, the energy losses are influential in the north. Between cases “b2” and “BI”, they have the same condition of WWR, but there is an additional attachment of the BIPvWt system, which strengthens the thermal performance, and there are also some shading effects of the BIPvWt system. Therefore, most cases show a decrease in total energy consumption, except for S.F., which has a mild climate (3C in the ASHRAE classification) compared to other cities. In the case of S.F., in some cases, “BI” consumes more energy compared to “b2”, which is explained by the shading effect of the additional installation.
From an orientation and energy consumption point of view, six cities showed common results. A south and southeast (SE) facing building consumes the least energy, but a north-oriented building requires the highest energy load because the heating energy loads in the six cities increase considerably. In addition, the deviation in N.Y. (14.0) and Copenhagen (14.3) far overweighs the other cities. In the case of N.Y., the effects of a BIPvWt installation on reducing the energy loads is significant because the WWR changes from 100% to 33%. On the other hand, in the case of Copenhagen, the deviation in each orientation is critical and highlights the need for careful consideration in an urban layout in the design guideline. Tokyo and Seoul, which show opposite aspects in south and north orientations, require discreet analysis in heating and cooling control.
In the case of PV energy generation, most cities tend to generate much more energy in a south-related face installation and the trend of the distribution is commonly predictable. In addition, in a detailed point of installation, the PV output can cover at least 3.9% (N.Y., north orientation) and at most 37.6% (S.F., south orientation) of the total energy consumption.
In the case of wind energy generation, the trend of the distribution appears to be irregular and varies according to the city and orientation. Therefore, in a detailed point of installation, the wind energy output can cover at least 0.8% (Seoul, northeast orientation) and at most 26.5% (S.F., west orientation) of the total energy consumption. In addition, compared to the PV cases, most cities have a relatively large standard deviation in each orientation, which explains why the wind direction and speed are much more random and highly erratic compared to the PV cases.
The total energy balance results show that each city can cover the following proportion of its energy consumption as an application of the BiPvWt system in average value: N.Y., 14.4%; S.F., 38.0%; Tokyo, 11.8%; Seoul, 8.9%; Copenhagen, 21.0%; and Amsterdam, 22.4%. Given the energy potential data, which ranges from 0.72 to 1.70 (Table 5), most urban areas may reduce their energy consumption briefly by approximately 8–38% after applying the BIPvWt system. Therefore, as a design guideline, a south facing layout of the energy consumption and PV output is required. On the other hand, the distribution of wind speed and direction differs from most cities and the urban layout even causes differences in the wind energy potential. Therefore, careful consideration and computer-aid approaches, such as CFD analysis, are needed to identify the most suitable turbine location prior to installation.

4. Conclusions

A feasibility simulation that evaluates a BIPvWt system in global regions was developed. The BIPvWt system can lead to a balance of the building energy consumption. The main findings can be summarized as follows:
  • The solar and wind energy potential shows a range of distributions in global 143 regions and a diagram of the distribution of the solar and wind energy potential is plotted. In 143 cities, the deviation of the energy potential ranges from 0.31 to 2.25.
  • The ASHRAE climate classification can explain the solar energy potential, but the wind energy potential, which includes speed and direction, shows relationships in similar regions or climate conditions.
  • As a design guide or engineering suggestion, arranging office buildings in south-related installation is effective for heating and cooling. In a PV installation, the south-related faces are much more efficient than the north-related faces. In the six cities simulated, the PV energy output varies approximately twofold at most depending on the region that is largely affected by the climate conditions, such as solar irradiation. On the other hand, the wind direction and speed in the six targeted cities follow the regional and seasonal conditions, which suggests that careful consideration and installation are feasible.
  • The BIPvWt system can cover 8–38% of the building energy consumption and has a leading advantage in energy saving in urban areas. In addition, as the WWR decreases from 100% to 30% through the application of BIPvWt, the heating, cooling, and lighting load decreases by 44.8% in the north of Copenhagen, 39% in the northeast of Amsterdam, 35.4% in the southwest of N.Y., 32.1% in the north of Seoul, 28.6% in the north of Tokyo, and 28% in south of S.F., respectively. As the proposed BIPvWt system is applied to the building envelope, there are many design considerations as well as a performance effect. Above all, the design will be similar to the BIPV system currently attached to the envelope. On the other hand, as there is a wind turbine inside the proposed system, additional factors, such as noise, weight, structural load, and vibration, will be need to be taken into account. Therefore, the design development of a BIPvWt and building design should be considered carefully along with building layout and enclosure design. This will also need to be considered in the future.
  • The coverage ratio is expected to increase with the development of PV and wind turbine technology and optimized building energy consumption, which suggests engineering and technological development of those systems. Also, generalization was needed for this study in order to view the overall energy potential in various regions and to review the feasibility of the proposed system, and therefore the target building was set to the highest skyscraper. The main reason for this is that if we set up a normal building in the simulations, there are various problems that can occur within the city. For example, shadows can be created and wind speeds may vary depending on the building layout or blocking by other buildings. In addition, considering that high-rise buildings are built inside the city center, the shadow of other structures and horizontal motion by wind can have a significant impact on the PV or wind energy production, which will be examined in a future study.
  • The total energy consumption will have the most significant impact on the energy contribution of the proposed PV and wind integration system. Therefore, the energy consumption ratios may vary according to how the input parameters, such as the building type, orientation, and HVAC (heating, ventilation, and air-conditioning) schedule, are set. Accordingly, it is important to select the appropriate input parameters. In addition, various design guidelines for urban areas have been released based on the local climate and building types; however, after careful consideration of potential renewable energy applications, building and urban design guidelines can be developed and harmonized based on the energy related fields.

Acknowledgments

This work was supported by INHA UNIVERSITY Research Grant.

Author Contributions

Jaewook Lee and Jeongsu Park has designed and written the manuscript under the supervision of Hyung-Jo Jung and Jiyoung Park. All authors have read and approved the final manuscript.

Conflicts of Interest

The authors declare no conflict of interest. The founding sponsors had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, and in the decision to publish the results.

Appendix A. City Information and Energy Potential

NoCountryCityArea (km2)Population (103)Density (km2)Total Potential *Solar Potential *Wind Potential *ASHRAE Classification
A01AustraliaAdelaide852114013001.281.181.383C
A02AustraliaBrisbane1972199910000.971.160.792A
A03AustraliaCanberra4724129001.061.210.914A
A04AustraliaDarwin216733000.951.260.651B
A05AustraliaMelbourne2543390615001.520.992.043C
A06AustraliaPerth1566175111001.311.291.333A
A07AustraliaSydney2037403620001.121.071.163A
A08BangladeshDhaka36015,66943,5000.651.080.211A
A09ChinaBeijing382021,00955000.680.920.444A
A10ChinaChongqing932721777000.310.470.153A
A11ChinaShanghai382023,41661000.680.920.443A
A12ChinaTianjin200710,92054000.630.850.414A
A14ChinaHong Kong275724626,4000.680.760.612A
A15IndiaBombay54617,71232,4000.721.080.371B
A16IndiaCalcutta120414,66712,2000.570.990.151B
A17IndiaDelhi207224,99812,1000.751.270.241B
A18IranTehran148913,53291001.081.410.763B
A19JapanTokyo-Yokohama854737,84344000.760.830.694A
A20KazakhstanSemipalatinsk21029914250.740.950.537
A21KoreaSeoul-Incheon226623,48010,4000.720.730.724A
A22KuwaitKuwait City712428360001.291.211.371B
A23MalaysiaKuala Lumpur1943708836000.530.810.241A
A24MongoliaUlaanbataar233123753000.871.030.77
A25NepalKathmandu60118019,8000.661.190.143A
A26New ZealandAuckland544135625001.740.992.493C
A27New ZealandRotorua89566300.9610.914A
A28New ZealandWellington18437020002.250.973.533C
A29North KoreaPyongyang176285016,2000.570.870.275A
A31PakistanKarachi94522,12323,4000.951.10.81B
A32PhilippinesManila158024,12315,3001.190.841.551A
A34Saudi ArabiaRiyadh1502566638001.081.440.721B
A35SingaporeSingapore518562410,9000.660.910.411A
A37Sri LankaColombo223218098000.991.150.831A
A38TaiwanTaipei1140743865000.810.810.812A
A39ThailandBangkok259014,99858000.781.020.551B
A40United Arab EmiratesAbu Dhabi88198211001.191.430.961B
A41UzbekistanTashkent531225042000.651.140.174C
A42Viet NamHanoi466371580000.540.870.211A
E01AustriaVienna453176339001.080.711.445A
E02BelgiumBrussels803208926001.040.561.514A
E03BulgariaSofia207119558000.540.660.435A
E04Bosnia and HerzegowinaBanja.Luka12381991610.490.790.184A
E05Czech RepublicPrague285131046000.970.591.365A
E07DenmarkCopenhagen453124828001.70.642.775C
E08FinlandHelsinki641120819000.830.631.036A
E09FranceParis.Orly284510,85838000.910.661.154A
E10GermanyBerlin1347406930000.950.631.275C
E11GreeceAthens583348460000.971.080.863A
E12HungaryDebrecen4612044430.680.780.595A
E13IrelandDublin453116026001.250.61.94A
E14IcelandReykjavik8018523001.850.543.166A
E15IsraelJerusalem23384036001.151.271.023C
E16ItalyRome1114390635001.080.941.213C
E17ItalyVenice13042633000.570.710.444A
E18LithuaniaKaunas15730119190.780.610.946A
E19NetherlandsAmsterdam505162432001.510.642.384A
E20NorwayOslo.Fornebu29097534000.550.60.56A
E21PolandWarszawa.Okecie544172032000.840.581.095A
E22PortugalLisboa1101266124001.291.131.453C
E23RomaniaBucharest285186065000.680.90.465A
E24Russian FederationMoscow466216,17035000.390.630.166A
E25SlovakiaBratislava11940034000.710.770.655A
E26SloveniaLjubljana5422541000.410.650.175A
E27SpainBarcelona1075469344000.90.960.843C
E28SpainMadrid1269615548000.861.080.643C
E29SwedenStockholm.Arlanda382148439000.730.640.826A
E30SwitzerlandGeneva18159933000.630.760.54A
E31TurkeyIstanbul136013,28798001.250.851.653C
E32UkraineKiev544294041000.70.760.645A
E33United KingdomLondon173810,23659000.720.660.794A
U01U.S.AK Anchorage22025111000.690.670.706A
U02U.S.AK Fairbanks85323800.630.780.488
U03U.S.AL Birmingham13737906000.851.090.623A
U04U.S.AR Little Rock6684316000.811.000.623A
U05U.S.AZ Phoenix3196419413001.011.510.512B
U06U.S.CA Arcata28186220.780.970.594A
U07U.S.CA Bakersfield35759017000.921.320.533B
U08U.S.CA Barstow-Daggett107232101.751.561.942B
U09U.S.CA Fresno44370316000.931.310.563A
U10U.S.CA Long Beach13346935000.871.230.513A
U11U.S.CA Los Angeles629915,05824001.001.210.783C
U12U.S.CA Sacramento1220188515001.091.270.913C
U13U.S.CA San Diego1896308616000.971.290.653A
U14U.S.CA San Francisco2797592921001.451.181.733C
U15U.S.CO Denver1730255915001.151.241.065B
U16U.S.DC Washington3424488914000.901.010.790
U18U.S.FL Miami3209576418001.121.111.121A
U19U.S.FL Orlando1958204010000.941.110.762A
U20U.S.FL Tampa2479262111000.951.200.692A
U21U.S.GA Atlanta685150157001.081.131.033A
U22U.S.HI Honolulu44084219001.351.241.471A
U23U.S.IA Des Moines5214899001.301.091.505A
U24U.S.ID Boise34735010001.001.200.805B
U25U.S.IL Chicago6856902313001.180.961.405A
U26U.S.IN Fort Wayne4453137001.170.941.395A
U27U.S.KS Wichita5574739001.591.211.984A
U28U.S.KY Lexington22829013000.960.980.944A
U29U.S.KY Louisville123510258000.951.030.884A
U30U.S.LA New Orleans65092214001.090.911.282A
U31U.S.MA Boston532544788001.470.981.965A
U32U.S.MD Baltimore1857226312001.041.031.064A
U33U.S.MI Detroit3463367211001.300.931.685A
U34U.S.MN Duluth1811207001.210.981.437
U35U.S.MN Minneapolis-St. Paul2647277110001.211.021.396A
U36U.S.MO Kansas City175615939001.421.131.714A
U37U.S.MO Springfield3682747001.141.091.184A
U38U.S.MO St. Louis239321869001.141.061.214A
U39U.S.MS Jackson6273806000.861.110.623A
U40U.S.MT Billings1371158001.441.131.745B
U41U.S.MT Helena42306661.001.110.906B
U42U.S.NC Charlotte191915358000.871.110.633A
U43U.S.NC Wilmington3472206000.981.090.873A
U44U.S.ND Fargo18117710001.501.041.966A
U45U.S.NE Omaha70272511001.181.011.365A
U46U.S.NJ Newark6327844241.140.971.314A
U47U.S.NM Albuquerque65081212001.341.461.234B
U48U.S.NV Las Vegas1080219120001.571.521.612B
U49U.S.NV Reno4253929001.101.380.835B
U50U.S.NY New York City11,64220,63018001.530.992.064A
U51U.S.OH Columbus1321148111000.890.920.864A
U52U.S.OK Tulsa8707028001.301.171.434C
U53U.S.OR Portland1357197615000.840.870.804A
U54U.S.RI Providence141212019001.120.951.285A
U55U.S.TN Memphis128711029001.011.110.913A
U56U.S.TX Austin1355161612000.961.100.812A
U57U.S.TX Houston4644576412000.921.050.792A
U58U.S.UT Salt Lake City720108515001.181.191.185B
U59U.S.VA Norfolk14024617331.351.051.653A
U60U.S.VT Burlington2331205001.070.921.226A
U61U.S.WA Seattle2616321812000.880.850.904A
U62U.S.WI Madison39140210001.110.981.245A
U63U.S.WV Charleston2541536000.760.980.534A
U64U.S.WY Casper71587941.741.222.266B
M01ArgentinaBuenos Aires268114,12253001.051.061.043A
M02BrazilRio de Janerio202011,72758000.811.170.451A
M03BrazilSao Paulo270720,36575000.670.890.452A
M04CanadaToronto2287645628001.20.911.496A
M05ChileSantiago984622563000.761.130.383C
M06ColombiaBogota492899118,3000.650.910.383C
M07EgyptCairo176115,60089000.991.210.772B
M08MexicoMexico City207220,06397000.91.050.743B
M09PeruLima91910,75011,7000.970.861.072A
M10South AfricaJohannesburg2590843233001.021.290.763C
* each "potential" represents relative size to the average.

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Figure 1. Histogram of 143 cities according to the American Society of Heating, Refrigerating, and Air-Conditioning Engineers (ASHRAE) classification.
Figure 1. Histogram of 143 cities according to the American Society of Heating, Refrigerating, and Air-Conditioning Engineers (ASHRAE) classification.
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Figure 2. Building module prototype for the energy simulation. (A) Detailed unit drawing; (B) basic module (b1); (C) basic module2 (b2); (D) building-integrated photovoltaic and wind turbine (BIPvWt) module (BI).
Figure 2. Building module prototype for the energy simulation. (A) Detailed unit drawing; (B) basic module (b1); (C) basic module2 (b2); (D) building-integrated photovoltaic and wind turbine (BIPvWt) module (BI).
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Figure 3. Diagram of the proposed BIPvWt system. (A) Detailed BIPvWt system drawing; (B) building envelope installation of BIPvWt.
Figure 3. Diagram of the proposed BIPvWt system. (A) Detailed BIPvWt system drawing; (B) building envelope installation of BIPvWt.
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Figure 4. Energy potential according to the ASHRAE classification. (A) Solar energy potential; (B) wind energy potential.
Figure 4. Energy potential according to the ASHRAE classification. (A) Solar energy potential; (B) wind energy potential.
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Figure 5. Total energy potential of the solar and wind source in global regions according to the population (see Appendix A for a more comprehensive list of abbreviations).
Figure 5. Total energy potential of the solar and wind source in global regions according to the population (see Appendix A for a more comprehensive list of abbreviations).
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Figure 6. Solar and wind energy potential in global regions (see Appendix A for a more comprehensive list of abbreviations).
Figure 6. Solar and wind energy potential in global regions (see Appendix A for a more comprehensive list of abbreviations).
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Figure 7. Photovoltaics (PV) energy output according to the envelope angle.
Figure 7. Photovoltaics (PV) energy output according to the envelope angle.
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Figure 8. Annual average PV energy output as a function of the solar irradiation.
Figure 8. Annual average PV energy output as a function of the solar irradiation.
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Figure 9. Power coefficient according to the wind turbine types [43]. (A) Sectional diagram of the wind turbine; (B) The generated power output of the wind turbine.
Figure 9. Power coefficient according to the wind turbine types [43]. (A) Sectional diagram of the wind turbine; (B) The generated power output of the wind turbine.
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Figure 10. Annual average wind energy output as a function of the wind potential.
Figure 10. Annual average wind energy output as a function of the wind potential.
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Figure 11. Chart of the energy consumption and generation according to the orientation. (A) New York City, (B) San Francisco, (C) Tokyo-Yokohama, (D) Seoul-Incheon, (E) Copenhagen, and (F) Amsterdam.
Figure 11. Chart of the energy consumption and generation according to the orientation. (A) New York City, (B) San Francisco, (C) Tokyo-Yokohama, (D) Seoul-Incheon, (E) Copenhagen, and (F) Amsterdam.
Energies 10 02158 g011aEnergies 10 02158 g011b
Table 1. Set point temperature for cooling (°C).
Table 1. Set point temperature for cooling (°C).
TimeWeekdaySaturdaySunday
06:00–18:00242427
18:00–22:00242727
22:00–06:00272727
Table 2. Set point temperature for heating (°C).
Table 2. Set point temperature for heating (°C).
TimeWeekdaySaturdaySunday
06:00–18:00212116
18:00–22:00211616
22:00–06:00161616
Table 3. Infiltration schedules (at 0 pa).
Table 3. Infiltration schedules (at 0 pa).
TimeWeekdaySaturdaySunday
06:00–18:000.250.251
18:00–22:000.2511
22:00–06:00111
Table 4. Statistical summary of the relative renewable energy potential.
Table 4. Statistical summary of the relative renewable energy potential.
RegionTotal (Solar + Wind)SolarWindSamples
MaxMinAVGS.D.MaxMinAVGS.D.MaxMinAVGS.D.
U.S.1.750.631.110.251.560.671.100.172.260.481.120.4663
Asia2.25 10.31 20.920.371.440.47 21.030.213.53 10.140.810.6938
Europe1.850.390.910.351.270.540.750.193.160.161.060.7232
Others1.200.650.900.181.290.861.050.151.490.380.750.3610
Total-0.32-0.23-0.60143
1 Wellington, 2 Chongqing.
Table 5. Description of the six targeted cities for a detailed simulation.
Table 5. Description of the six targeted cities for a detailed simulation.
CityArea (km2)Population (Thousands)Density (people/km2)Relative Energy PotentialASHRAE Classification
TotalSolarWind
New York City11,64220,63018001.530.992.064A
San Francisco2797592921001.451.181.733C
Tokyo-Yokohama854737,84344000.760.830.694A
Seoul-Incheon226623,48010,4000.720.730.724A
Copenhagen453124828001.700.642.775C
Amsterdam505162432001.510.642.384A
Table 6. Statistical description of energy consumption and generation in the six cities (kWh/(m2·y)).
Table 6. Statistical description of energy consumption and generation in the six cities (kWh/(m2·y)).
CityEnergy ConsumptionEnergy GenerationTotal
LightingHeatingCoolingPVWind
AVG 1S.D. 2AVGS.D.AVGS.D.AVGS.D.AVGS.D.AVGS.D.
N.Y.12.92.19.88.529.910.7−3.81.6−2.11.149.714.0
S.F.12.01.80.50.96.54.0−4.42.0−1.71.816.05.4
Tokyo13.11.86.66.621.76.8−3.51.5−0.60.339.49.8
Seoul12.62.115.710.819.85.6−3.01.4−0.60.246.212.7
Copenhagen15.22.419.012.92.71.4−2.91.2−2.92.234.014.3
Amsterdam14.52.611.79.24.62.2−3.01.3−2.51.928.110.4
1 Average, 2 Standard deviation.

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Lee, J.; Park, J.; Jung, H.-J.; Park, J. Renewable Energy Potential by the Application of a Building Integrated Photovoltaic and Wind Turbine System in Global Urban Areas. Energies 2017, 10, 2158. https://doi.org/10.3390/en10122158

AMA Style

Lee J, Park J, Jung H-J, Park J. Renewable Energy Potential by the Application of a Building Integrated Photovoltaic and Wind Turbine System in Global Urban Areas. Energies. 2017; 10(12):2158. https://doi.org/10.3390/en10122158

Chicago/Turabian Style

Lee, Jaewook, Jeongsu Park, Hyung-Jo Jung, and Jiyoung Park. 2017. "Renewable Energy Potential by the Application of a Building Integrated Photovoltaic and Wind Turbine System in Global Urban Areas" Energies 10, no. 12: 2158. https://doi.org/10.3390/en10122158

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