1. Introduction
Building level microgrids have become a topic of increasing relevance for the integration of onsite energy sources in the interest of energy resilience and load management [
1], [
2]. The growing prevalence of native direct current (DC) devices, coupled with concerns for efficiency and power quality have led to isolated power distribution architectures involving DC or otherwise asynchronous current [
3], [
4]. The presence of an isolated microgrid at the building level may enhance the feasibility of small-scale generation from energy harvesting sources which are traditionally considered unworthy for integration with the synchronous utility grid. Energy harvesting from alternative sources enhances generation diversity, enabling levels of autonomy and resilience that are unattainable when solar, storage and utility supply are the only available resources.
Energy harvesting options in buildings are frequently assessed in the literature with detailed focus on a given resource, technology, or application. Few studies however - with the exception of Matiko et al. [
5] - have endeavoured to develop a comprehensive resource assessment, which is the goal of the present work. The following sections provide a review and quantification framework for the available energy harvesting resources in buildings. Current and future technology limitations are discussed, and the framework is applied to a high-performance commercial building model to characterize the various resources.
This work does not intend to provide an exhaustive review of specific energy conversion technologies, but rather to provide a summary of available energy resources and pertinent technologies, with speculation about the future potential for application in buildings. The resources are limited to those which are readily converted into the electrical domain. Energy sources harvestable in the thermal domain will be addressed in a follow-up work.
1. Energy Resources in Buildings
At a high level, a building may be considered an open thermodynamic system, which exchanges energy with its surroundings via three main mechanisms: the exterior environment, occupants, and concentrated utility inputs. This concept is presented in
Figure 1, where the building system boundary may be considered to include exterior surfaces and a finite surrounding air volume.
In this depiction, Ein comprises energy added to the system from environmental sources and utility inputs. Wint denotes the internal work done in the system, which is equivalent to the total energy consumed for end-use functions such as lighting, space conditioning, etc. This can also be considered the traditional energy demand of the building. Eint represents the energy generated internally from building occupants, as well as internal dissipation of environmental energies and utility sources in the execution of useful work. The latter two of these sources can cumulatively be denoted Erec, or recyclable energy. Eout represents the balance of energy that is dissipated to the surroundings. In this representation, the internal energy of the building system cannot be easily described by a single state function, which complicates any effort to produce a steady-state energy balance. However, the thermodynamic components described can be broken down as follows in Equations 1 through 3,
With reference to this framework, energy harvesting can be employed to maximize the proportion of
Eenv and
Eint which can be utilized for useful work (
Wint) such that
Eutil and
Eout can be minimized. Of course useful work should not be considered a harvestable resource, as this action would increase the necessary input energy to overcome harvesting inefficiencies, ultimately affecting demand negatively. The generalized components of
Ein and
Eint can be further broken down into specific resource categories, as depicted in
Figure 2.
With the specific resources identified, the total energy generated from energy harvesting, Egen, may be approximated by Equation 4,
where
Eresource describes the total energy associated with specific resources
Ri - R, Capp is an application coefficient which describes the amount of resource accessed by a given energy harvesting application, and
η harvester is the conversion efficiency of a given harvesting technology. The total available electrical energy from harvested sources in a building can thus be estimated via a 3-step process, involving a) approximation of the total resource magnitude, b) determination of a feasible accessibility ratio in each energy harvesting application, and c) consideration of the conversion efficiency of selected harvesting technology. The following sections will elaborate on the specific resources identified, and the state-of-the-art technologies available for harvesting.
Solar
The solar energy resource is comprised of electromagnetic radiation in the spectrum of 300-1100 nm. The magnitude of this resource is best evaluated on an annual interval due to seasonal and diurnal variability. A sun path diagram for the case study location of Toronto is presented in
Figure 3, which indicates the variation in relative position and duration of sun exposure over the course of a year.
The magnitude and variability of the solar resource at a given location depends predominantly on latitude, sky clearness and the orientation of the collection surface, commonly denoted the plane of array. The available resource on a given collection surface can be defined as the sum of the direct beam irradiance, diffuse irradiance and ground reflected irradiance, in accordance with Equation 5,
where
POA represents the plane of array irradiance, with the various components denoted by their respective subscripts. The method by which the components can be derived varies dependent on the available data, as described by Lave et al. [
6]. The process is simplest when a diffuse horizontal irradiance (DHI) data set is available for a given location in addition to the more commonly available global horizontal irradiance (GHI), as is the case with most EnergyPlus TMY weather files [
7].
In this simplified case the direct beam component may be derived as a function of the local direct normal irradiance (DNI) and angle of incidence (AOI) between the collection surface and the sun rays as described by Equation 6,
where
DNI is the direct normal irradiance. The angle of incidence can be described by the geometry of the sun path and plane of array per Equation 7,
where
θZ and
θAS are the instantaneous solar zenith and azimuth angles respectively, and
θT and
θAA are the array tilt and azimuth angles, respectively. While the array terms are a result of design geometry the solar terms are a function of the annual sun path relative to the given global location. These can be derived from a number of modelling libraries such as pvlib [
8] or from first principles, as presented by Hailu and Fung [
9].
The ground reflected irradiance component can be described as a function of the local albedo, or solar reflectance in accordance with Equation 8,
where
α is the local albedo. Finally, the diffuse component of radiation can be derived generally as a function of the view factor from the collection surface to the sky and the irradiance profile of the sky. The latter term is somewhat complex and may be approximated from a variety of diffuse irradiance transposition models. In a comparative analysis of these models, Loutzenhiser et al. [
10] show the Hay-Davies and Perez models to be generally most accurate. Both models are anisotropic, with the primary difference being the inclusion of a horizon brightening component, as provided in the Perez model.
Table 1 presents the annual magnitude of the solar resource for building surfaces at cardinal directions and typical orientations for the case study location of Toronto, derived via the pvlib toolset with the Perez transposition model.
In urban environments, the solar resource is variably affected by shading from neighbouring buildings and additional structures. In this case, a shading factor may be applied to the surface area in question, or ideally a detailed shading analysis may be conducted based on exact local and neighboring geometries.
Artificial Light
The other radiative resource in buildings is artificial light which is generally designed in reference to desired illuminance or lux, a function of the human eye’s response to visible spectrum radiation. Lumens can be translated to equivalent watts of radiation with reference to the photopic curve, which defines the human eye response spectrum. With reference to the photopic conversion, Dai et al. [
11] show achievable luminous efficacy from high-efficiency LED lighting in the range of 400 lumens per watt provided that constraints relating to colour temperature are upheld. Taking the inverse of this luminous efficacy term allows an approximation of the available radiant energy in a space dependent upon the lighting intensity. For example, in an office space with design lighting intensity of 400 lux at desk level, the available radiant energy, presuming Dai’s high efficiency lighting would be 1 watt/m
2. Non-LED lighting technologies exhibit lower luminous efficacy, which indicates greater available energy. However, much of the radiant energy of an incandescent bulb for example, is emitted in the infrared spectrum which is not readily accessible for electrical conversion. By contrast, the spectrum of high efficiency lighting is inherently concentrated within the accessible range of common photovoltaic devices.
Wind
The wind energy resource is a form of kinetic energy associated with the motion of air in accordance with global thermal gradients and weather patterns. Like the solar resource, wind energy experiences seasonal variation with larger magnitudes typically observed in winter seasons due to larger temperature gradients in atmospheric air masses. A given location may experience a prevailing wind direction from which most of the wind resource acts, however wind can be expected to act from all directions throughout the course of a year, especially in urban environments where neighboring obstructions have dominant influence. A wind rose diagram for the case study location of Toronto is presented in
Figure 4.
The available power in a wind resource described on a per unit area basis by Equation 9,
where
Pwind is the instantaneous wind power per unit area,
ρ is the fluid density,
v is the velocity. For a given altitude, air density is a function of temperature and humidity, which lends further to the winter bias in availability. Due to the relatively minimal influence of humidity at standard outdoor temperatures, a dry air assumption can be employed to approximate the effective density as a function of temperature in accordance with Equation 10,
where
p is the absolute air pressure,
R is the specific gas constant for dry air and
T is the air temperature. Wind speed can be generally derived from typical year weather data at a given location but can be expected to vary significantly over small distances. Once a data set is acquired, a height adjustment is generally required to determine the effective wind speed at the height of interest. The relationship between wind speed and height above the surface depends on the roughness of the surroundings, and is most commonly estimated with the power law, defined in Equation 11 [
12],
where
v is the wind speed at height
z,
vref is the known wind speed at height
zref, and
α is the wind shear coefficient for the location of measurement. For rough calculations the average height of a catchment area may be utilized, however due to the non-linear nature of this relationship, it is more accurate to segment the area into height increments for areas spanning large ranges, such as tall commercial buildings. The wind shear coefficient can be assumed at an average of 0.25 in urban conditions [
13].
Wind velocity can be further altered by interaction with building geometries. Initially, a large portion of the kinetic energy will be translated into static pressure, ultimately dissipating as vibration and mechanical strain in the building structure. In the laminar domain, flow affects include deceleration due to boundary layer friction at the building surface and acceleration around exterior corners. The latter has been described by You et al. as a function of the flow velocity ratio [
14]. Flow interactions with geometric objects can also produce a transition to the turbulent domain. Turbulence is characterized by disordered kinetic energy, having inherently limited harvesting potential. In urban environments upstream flows may be largely turbulent in advance of interactions with a given building structure because of neighboring buildings. These affects interact differently depending on the specific local geometry of the building to influence the effective wind speed at any given unit area around the building exterior.
The static pressure component of wind energy has value in buildings in its capacity to drive natural ventilation. Ventilation system energy demand may be reduced if ventilation is enabled via wind pressure gradients. There are generally seasonal constraints to this approach in cold climates, however these may be addressed with passive energy recovery ventilation approaches, as proposed in the literature [
15], [
16].
For the purposes of available energy assessment, the total magnitude of the wind resource available at a building can be considered with reference to Equation 9. The average wind speed upstream of a building is approximated based on the local weather data and height compensation via the power law. The relevant catchment area can be defined instantaneously as the cross-sectional area of a building in the plane normal to the instantaneous direction of wind speed. The resultant power calculation can be integrated over a typical annual interval to determine the total annual resource. The geometrical relations of the instantaneous catchment area are represented as a function of wind direction in
Figure 5.
The width of the catchment area is defined by Equation 12, as a function of the wind direction,
where
WWA is the wind catchment area width,
W0 is the base building width defined in the east-west plane,
L0 is the base building length defined in the north-south plane and
θWD is the angular wind direction in degrees east of north, per EnergyPlus data conventions. For buildings with a base orientation offset from due south, a relative static offset may be applied to the wind direction.
As with the solar resource, this fundamental assessment will often be implicated due to flow effects from upstream geometries. These effects may be accounted for with a simple modification to the catchment area, however computational fluid dynamics (CFD) modelling should be employed for most accurate assessments of the interactions with urban environments and neighbouring geometry. The monthly wind resource density at a height of 20 m, based on Toronto’s Billy Bishop Airport weather data is presented in
Figure 6, in contrast to the monthly solar resource. Note that the unit area referenced in
Figure 6 is not constant for the two resources; the solar resource represents the sum of 5 cardinal building surfaces, while the wind resource is quantified with respect to the instantaneous catchment area, described above.
Vibration
Structural
In locations prone to seismic activity, ground vibrations may occur periodically in large magnitude. However, in the absence of seismic events smaller magnitude ground vibrations are often present due to anthropogenic activity in the surroundings including vehicle traffic and construction [
17]. Buildings may also experience vibrations induced from internal machinery and HVAC equipment, as well as the motion of occupants. In the case of tall, slender buildings wind induced oscillation are also present.
Energy in vibrations can be described as a combination of kinetic and elastic energy forms oscillating sinusoidally at phase angles of 180° with respect to each other. In most cases, the kinetic energy of ambient ground vibrations is too small to be observed by human sensory but may be observed with accelerometers. The elastic energy manifests as elastic strain in the structural materials of the building.
The magnitude of the vibration resource at a given location is difficult to determine from readily available data sources such as weather files. However, extensive work exists in the literature on the understanding and attenuation of structural dynamics. Valera et al. have shown that for a medium rise building, the largest contributors to structural vibrations were ground motions from vehicle traffic and internal vibrations from air-conditioning equipment, at peak frequencies 8 and 29 Hz, respectively. Roundy et al. [
18] note available energy density in the range of 50-250 μW/cm
3 from common ambient vibrations in buildings with reference the volume of a harvesting device. Priya [
19] defines the maximum power available in a vibrating mechanical system in accordance with Equation 13, which stems from the original analysis provided by Williams and Yates [
20],
where
a is the magnitude of the excitation acceleration,
ωn is the system natural frequency,
m is the proof or seismic mass of the system and
ζ is the damping ratio. This relation critically assumes the excitation vibration is an infinite source of power with a mass that is much greater than the seismic mass of the generator. For ground-based vibrations it can be assumed that the building acts effectively as a seismic mass with externally induced vibration, in which case, Priya’s relation may apply provided that the energy harvesting devices are structurally integrated.
For a structurally integrated energy harvesting, the effective seismic mass can be considered the modal mass of the relevant structural body’s experiencing vibration. Modal mass is defined as the fraction of mass which is effectively resonant - about 25% of total mass for beams with fixed supports. The damping ratio in building structures as described by Valera is quite low at around 2% for concrete. Frequency and acceleration magnitudes describe the excitation.
In cases where vibrations are present in large magnitudes from either seismic or wind loading conditions, buildings will often employ tuned-mass dampers as attenuation mechanisms. In order to function successfully the damping devices are required to dissipate large amount of energy as heat, which may be otherwise available for energy harvesting, as presented by Petrini et al. [
21].
Equipment
Machine-based vibrations are a result of internal rotating unbalance. In the literature, these types of vibrations are well documented from the perspective of vibration damping, however there is limited work aimed at deriving the total available power. With reference to fundamental dynamics, the forcing function of a rotating unbalance is a function of the rotating mass and eccentricity internal to the machine [
22]. These details are of course difficult to acquire for any given machine, thus the key interest to the present work is the ability to derive the total available power with reference to readily available characterization data, such as the machine’s total mass, acceleration amplitude, and frequency of vibration. Many articles considering energy harvesting from machine vibrations, consider only small seismic masses which do not affect the excitation vibration, and are thus limited in their harvesting potential. Wang and Inman [
23] provide a review of approaches to vibration damping which endeavour to achieve optimal results in the contexts of both energy harvesting and vibration suppression, indicating the trade-offs present between the two objectives. Bulsara et al. [
24] show that losses for experimentally applied unbalances can exceed 50% of balanced energy consumption for a given rotating speed and relate the power losses to unbalance at an average of 0.11 W/g-mm. However, rotational unbalance is generally considered an undesirable quality from the machine design perspective, and thus the results of Bulsara can be interpreted as an extreme representation.
Two methods exist to approximate the available energy. The first is a top-down approach which considers the energy of vibration as a loss mechanism of the input energy and thus relates to the efficiency of the machine. The second is a bottom-up derivation based on the vibration dynamics. As the model presented by Williams and Yates assumes the excitation power to be infinite, it cannot apply.
Assuming damping effects are negligible, a vibrating machine can be considered as a simple spring-mass system under a periodic excitation force. The energy of a given cycle can be equated to the peak kinetic energy as described by Equation 14,
The power dissipated in the system can then be described as a function of the forcing frequency, f, in Hz, per Equation 15,
In the literature, vibrations are typically characterized by peak acceleration, amax, and frequency, f. As velocity can be defined as the integral of acceleration over time, and the acceleration can be characterized as a sinusoidal function, the relationship between peak velocity, max, and peak acceleration can be described by Equation 16,
Substituting Equations 14 and 16 with Equation 15 yields the following derivation for available power in a spring mass system under forced vibration:
Applying the above formula to an example from Priya involving a 5 HP machine with peak acceleration of 10 m/s2, frequency of 70 Hz, and assumed mass of 2000 kgs, produces 36 W of available power, or roughly 1% of the rated machine power. In the interest of simplifying this analysis it is assumed going forward that the available power from relatively well-balanced vibrating machinery is on the order of 1% of the machines total demand.
Potential
Potential energy is a particularly relevant resource in tall buildings, due to large variations in height. The two mechanisms explored herein are micro hydro and elevator regeneration.
Micro Hydro
The potential energy available from stormwater collected on a building’s rooftop can be approximated based on gravitational potential in accordance with Equation 18,
where
ESH is the stormwater hydro energy,
V is the volume of water retained on the roof,
is the density of the water,
g is the acceleration due to gravity, and
z is the height of the storage reservoir or roof. Over the course of a year, the annual resource can be approximated with reference to the average annual precipitation in a given location. The resource can then be normalized on a per unit roof height basis, as follows:
where
Pr is the annual precipitation, and
Aroof is the roof area.
In many cases, the more significant hydropower resource in a building may be greywater, which is characterized as wastewater from domestic use which is free of solid organic waste. The difficulty with this approach in many North American buildings is the lack of separation of greywater from blackwater in plumbing systems. McNabola and Corcoran have examined the potential of micro hydro at the municipal scale, from both policy [
25] and technical [
26] perspectives. Their analyses focused on deployment of microhydro facilities in place of flow regulation valves commonly utilized to control downstream pressure, ultimately showing that in a case study of Dublin, Ireland, microhydro could produce up to 7.5 GWh/yr from roughly 1 MW of installed capacity. In the building context, Santillan [
27] presents a detailed analysis of the potential and limitations of hydropower in a residential high-rise incorporating both stormwater and grey water drainage. In this work, Santillan shows that roughly 75% of water use in a residential setting ends-up as grey wastewater. Based on the presented data, it can be assumed that in a commercial context, the proportion is closer to 50%.
In Canadian residential settings annual water consumption is on the order of 220 L/pp/day [
28] while in commercial settings it has been characterized according to floor area at roughly 55 L/ft
2yr when cooling tower consumption is omitted [
29]. The resultant total annual consumption volume can be applied in Equation 18 to estimate the annual resource, where the relevant height value is the midpoint of the building which accounts for the averaging of gravitational potential of flows evenly distributed throughout a building.
Elevators
Energy harvesting from elevator motion works akin to the concept of regenerative braking in electric vehicles. When the potential, or momentum of a mass is driving its motion, the powertrain can be switched into reverse such that the driving motor works as a generator and the electromotive resistance in its windings provides a braking force to the mass in motion. This resource is of particular interest due to the prevalence of this regenerative braking capability in modern elevators, which is often forgone in design due to the complexity of integration with building power systems.
A detailed study of the available energy from energy regeneration was conducted by Nobile et al. [
30], showing that the total recoverable energy for a single elevator trip can exceed 50% of the motor input energy after factoring mechanical and motor losses. However, the recoverable energy also varies depending on the number of passengers, direction of travel, and distance of travel. Nobile et al. categorize elevator trips into 4 types according to the ratio of passenger weight to counterweight and direction of travel. Generally, energy is harvestable only when the descending mass exceeds the ascending mass. An annual simulation of harvested energy based on audited elevator usage data from a 6-story condominium building shows that recovered energy equates to roughly 20% of the total input energy for the elevator on an annual basis. The authors note that this value may vary with usage patterns.
Without detailed traffic data for a building in question, it is considered sufficient to extrapolate this 20% recovery model to estimate annual resource based on the annual elevator demand, which can be derived from a building energy model. Detailed model derivations for elevator energy consumption that might be adapted for finer analysis in future work are presented by Tukia et al. in [
31] and [
32]. As a rule of thumb, elevators can be expected to account for 3-8% of energy consumption in buildings [
33], with dependence on building height, occupant density and travel frequency.
Occupants
Occupants dissipate energy into a building in many forms, including kinetic, acoustic as well as sensible and latent heat. Of interest in the present work is the kinetic energy imparted by occupants into the building, in the forms of exercise and traffic across doors and floors.
Fitness
The energy exerted by humans during indoor cardiovascular exercise is typically dissipated via friction and heat in the context of stationary bikes, elliptical and rowing machines. A detailed review of the energy available from a variety of human powered fitness machines is given by Chalermthai et al [
34]. The results of which are summarized below in
Table 2.
Annual generation profiles from the various machines may be derived akin to the load models employed by building energy simulation tools such as EnergyPlus, where the active power is extrapolated over time according to an activity schedule. This approach would be most effective in a commercial gym where occupancy insights are available. Over an annual scale, simplifying assumptions can also be made with regards to the number of building occupants and average hours spent exercising in the building’s gym per week.
Doors
A physics-based analysis of the energy generating potential of swing and revolving doors is given by Partridge & Bucknall [
35] who show that the generation potential is a function of door geometry, mass, and mechanical losses due to damping and hardware friction. Ultimately a generalized metric is provided indicating that average revolving doors may produce up to 40 J of energy per person, while swing doors have less available at closer to 10 J.
Gilani et al. [
36] produced a lightweight prototype of an energy harvesting revolving door and observed average energy generation of 16 J per push. It is expected that the lower output relates to the limited mass of the door in comparison to the physics-based analysis provided by Partridge and Bucknall. Gilani et al. applied their results to a case study involving a busy mall application where it was theorized the door would rotate a maximum of 38,000 times per day for annual energy generation of 61 kWh/yr.
Extrapolating the per revolution energy data to annual generation profiles generally follows the same method of the fitness machines where a typical traffic schedule is implemented at each door in question. On the annual scale, the available resource can be predicted in accordance with an average number of revolutions or openings per day in accordance with the method presented by Gilani.
Walking Motion
During human walking motion peak forces transferred to the a floor are described by Puscasu et al. [
37] as roughly 20-30% greater than body weight. In their analysis, Puscasu et al. relate this to the deflection observed in a floor tile to determine the mechanical energy transferred per step, which they show is on the order of 1 J/step for average body weight of 76 kg and 1-3 mm deflection in the floor tile. These data points can be extrapolated to determine the total available energy due to walking motion as a function of the space occupancy and steps per hour per occupant. Clemes et al. [
38] have shown that the mean step count for office workers during a workday is on the order of 4000 steps, which can be translated to 500 steps per hour assuming an 8-hour work day. With these data points the available walking resource can be extrapolated on the order of 500 J/h, occupant or roughly 1.1 Wh per occupant per day.
Thermal
Thermal energy is a significant resource in buildings. In Toronto’s climate, space and water heating comprise up to 80% of residential energy demand [
39]. For waste thermal energy to be converted into useful work there must be a gradient present, or a source of heat flow. The fundamental limitation of useful work that can be derived from two thermal reservoirs at different temperatures is described by the Carnot efficiency, per Equation 20,
where
Th is the temperature of the hot reservoir,
Tc is the temperature of the cold reservoir and
ηc is the Carnot efficiency. This relation indicates that the magnitude of available resource in any given case is proportional to the temperature delta between the two reservoirs. A given thermal resource can be estimated with reference to the Carnot efficiency by determining the rate of the heat flow across the gradient. Heat flow can generally occur in either conductive, convective, or radiative mechanisms. Conduction is presented in Equation 21, for example,
where
Q is the rate of heat transfer,
U is the effective thermal conductance between the reservoirs and
A is the area through which the heat is transferring.
The thermal resources that exist in buildings are generally considered components of end-use functions. For example, the heat flow across a building envelope should be minimized rather than harvested, and the heat delivered to, or removed from a space should be unhindered as to maximize the efficiency of delivery. However, thermal energy that is purposely expelled from the building is a form of energy loss that is considered a desirable resource for energy harvesting.
For waste heat applications, consideration must be given to the annual variation in thermal gradient associated with instantaneous outdoor temperatures. On an annual scale we can relate the total available resource to the energy that is expelled by the ventilation system, which relates to the energy recovered by the ventilation system according to the system heat/energy recovery efficiency. There is also a resource present in the heat that is expelled by a building’s cooling system, provided that efforts to harvest this particular resource do not interfere with the rate of expulsion. These two resources are described by Equations 22 and 23,
where
QEx is the heat resource expelled from ventilation,
QR is the heat recovered in ventilation and
ηR is the efficiency of heat/energy recovery. In Equation 23,
QC represents the heat resource expelled from cooling,
EC is the energy demand of the cooling system and
COPC is the system level cooling coefficient of performance.