1. Introduction
Increasing energy demand, fossil fuel depletion, and environmental concerns with the use of fossil fuels drive the present society towards renewable energy use [
1,
2,
3,
4,
5]. Abundant in nature and renewable, solar energy has been increasingly used in recent decades [
3,
6,
7,
8]. However, the efficiency of solar to electricity conversion technologies is still a concern for a promising future [
9,
10,
11,
12]. Thus, hybrid systems utilizing all ranges of solar radiation spectrum are gaining popularity for electricity, heating, cooling, and solar fuel production through thermoschemical processes [
13,
14,
15]. Moreover, several studies have been performed to show that the multigeneration systems are capable of energy production in comparison to standalone configurations [
16,
17,
18]. Organic Rankine Cycle (ORC) power systems are proved to be one of the promising technologies for the exploitation of low-temperature energy sources [
19].
Wang et al. [
20] reported the experimental analysis of a solar-based organic Rankine cycle (ORC) having both flat plates and evacuated tube-based collectors for low-temperature applications. The obtained results of this system revealed an isentropic efficiency of 45.2%, providing a mechanical power output of 1.73 kW.
Wang et al. [
21] studied flat plate collectors with an ORC cycle for three conditions including power generation, combined heat, and power (CHP) and combined cooling and power (CCP) model. The results showed the maximum power generation of this system is in the power mode and CHP mode. Wang et al. [
22] examined an energy optimization of a flat plate solar collector with an ORC for the combined generation of cooling, heating, and power (multigeneration system). NSGA-II algorithm was applied to optimize the total heat transfer area and the power production.
Calise et al. [
23] reported the performance of a hybrid system based on solar energy, geothermal energy, and an auxiliary boiler, for the combined production of cooling, heating, power, and freshwater purposes. The results of this study demonstrated the maximum exergy efficiencies of about 50% and 20%, when operating in the heating and cooling mode, respectively.
Bellos and Tzivanidis [
24] reported examination of an ORC based hybrid system with an ejector device, with 87% and 12% energy and exergy efficiencies, respectively. Gogoi and Saikia [
25] studied a combined system having a solar-based ORC cycle and an absorption cooling system, considering five different working fluids for the environmental conditions of Jaipur, India. They concluded that the system provided a net power up to 1.7 MW in February with R245fa as the working fluid, and a maximum cooling of 6.0 MW was obtained with Neopentane.
El-Emam and Dincer [
26] examined a hybrid system driven by solar energy and biomass to produce hydrogen, electricity, and supply cooling. The outcome of this study showed the energy and exergy efficiencies of 40% and 27%, respectively for this hybrid system. Khalid et al. [
27] investigated a hybrid system using biomass to supply power, hot water, and space cooling/heating. They report thermal and exergy efficiencies of 91% and 35% for this cogeneration system, respectively.
El-Emam and Dincer [
28] examined a novel hybrid system consisting of a solar tower, a Rankine power cycle, an electrolyzer, a desalination unit, and an absorption chiller. The proposed system supplied cooling, heating, and power; moreover, it was capable of freshwater and hydrogen production. They reported the maximum energy and exergy efficiencies were 40% and 30%, respectively. Utilization of waste heat of photovoltaic/thermal (PV/T) systems in a thermoelectric-based electrolyzer for hydrogen production was proposed by Behzadi et al. [
29]. The exergy efficiency of up to 12.01% was obtained for this system.
Moaleman et al. [
30] proposed a system that produces power and heating by the integration of thermal collectors and a linear Fresnel reflector. The results revealed the yearly production of cooling, heating, and power generation of 3944, 6528, and 2290 kWh, respectively for this system.
Exergoenvironmental analysis of any power system to evaluate the exergy-based cost of unit power is recent, and most of the previous studies on hybrid systems have not been paid much attention to it. A detailed exergoeconomic and exergoenvironmental analysis of a solar combined cycle system by Cavalcanti [
31] indicated that the solar field could help to increase the electricity production by 4.2%, reduce the costs production by 2.6%, and decrease the exergy based environmental impact by 3.8%.
Table 1 summarizes the key points of each research.
Pertinent literature reveals that attempts have been made to design, develop, and analyze hybrid systems using carbon-free renewable energy sources for cooling, heating, and power (CHP). Further, a few applications were also coupled with the CHP system to produce freshwater, hydrogen, and in limited cases syngas. The present proposed system goes also in the direction of the increasing use of renewable energy sources. However, limited studies existed in literature about the combined use of solar and wind energy sources in Ref. [
32], but the production of syngas from the combination of renewable energy sources has not been investigated yet. Further, in most of the previous studies, systems’ efficiency was limited to energy and exergy only. The addition of economic and exergoenvironmental assessment of the proposed hybrid system gives additional relevance to this study. The system under consideration is said to be hybrid as it is based on a combination of renewable energy sources. The innovations of this research are as follows:
Developing the new hybrid system consisting of the solar and wind energy resources
Producing electricity, cooling, and syngas by this hybrid cogeneration system
Energy, exergy, economic, and exergoenvironmental (4E) analyses
2. Mathematical Modeling
2.1. System and Process Description
Figure 1 is a schematic diagram of the proposed system, the arrows also illustrating the process. The proposed system comprises six subsystems: solar dish, ORC, single-effect absorption chiller, proton-exchange membrane (PEM) electrolyzer, wind turbine, and methanation plant. The working fluids in the solar dish, ORC, and absorption chiller subsystems are Terminol VP-1, R134a, and lithium bromide solution, respectively. Terminol VP-1 is capable of operating under pressures of 15 bar and temperatures up to 400
[
33]. R134a exhibits the highest energy and exergy efficiencies for the ORC system [
33,
34,
35]. Water, as a refrigerant and lithium bromide as an absorbent, is one of the most used working fluid pairs in the absorption chillers [
36].
Terminol VP-1 passes through a solar dish collector to absorb the solar radiation heat (1). A thermal energy storage tank is used to attenuate the fluctuations of solar radiation and for the system’s operating even during the night and to the operating fluid reach the desired temperature. The thermostat I avoids sending the Terminol at temperatures lower than 80 to the ORC’s evaporator. When the Terminol temperature is under 80 , it can be pumped through the bypass line back to the storage tank, and when it is over 80 it is pumped to the evaporator (2) of the ORC subsystem to heat the ORC working fluid. The superheated R134a enters the turbine (9) to generate power, then it passes through the condenser and it is pumped back to the evaporator to close the ORC. The electricity produced from the ORC subsystem provides part of the electricity needs in the methanation subsystem; the remaining electricity can be used to supply the electric loads or even sent to the electric grid. Thermostat II avoids sending the Terminol at temperatures lower than 60 to the absorption chiller’s generator. When the Terminol temperature is under 60 , it is sent back through a bypass line to the storage tank, and when its temperature is over 60 it enters the absorption chiller’s generator (3) to provide the heat required for the cooling products in the evaporator.
Wind turbines produce part of the electricity required by the electrolyzer. The hydrogen produced in the electrolyzer enters the methanation plant (19), where it reacts with supplied CO2 (A2) to produce CH4 syngas (A3) and steam (A4). In this way, the syngas (that has many useful applications) production is fully based on renewable sources. Besides that, cooling and power are produced simultaneously by absorption chiller, ORC, and wind turbines, respectively. Additionally, the heat released by the condenser of the absorption chiller and by the ORC condenser, oxygen released by the electrolyzer, and steam released by the methanation plant can be useful for any purpose.
The following main assumptions are considered in the system’s modeling and simulation:
The solar radiation and wind turbine modelling are presented in
Appendix A.
2.2. Mass and Energy Balances
The following reaction occurs in the electrolyzer for water splitting [
42]:
The performance of the electrolyzer can be obtained from the following equation [
42,
43,
44]:
As the voltage efficiency of the PEM is assumed to be 72%, an operational voltage of 1.74 V is achieved. The mass flow rate of the produced hydrogen can be expressed as [
42,
43,
44]:
where F represents the Faraday’s constant, 96,495 C/mole, and subscript elec denotes electrolyzer [
42,
43,
44].
The reaction that happens in the methanation plant can be expressed as:
The Coefficient of Performance (COP) of the absorption chiller is defined as:
where subscripts Eva, Gen, and p denote evaporator, generator, and chiller’s pump.
Mass and energy balances and energy efficiencies for each component of the proposed system are summarized in
Table 2 [
34,
40,
41,
45,
46,
47].
In
Table 1, T, h,
, and
denote temperature, specific enthalpy, constant pressure specific heat, and mass flow rate, respectively.
and
represent power and heat transfer rates.
is polythrophic efficiency. Subscripts E, T, C, and elec refer to evaporator, turbine, condenser, and electrolyzer, respectively. HHV stands for the higher heating value.
The energy efficiency of the whole system can be set as:
where subscripts E, T, P, and elec refer to the evaporator of the absorption chiller, turbine of the ORC, pumps, and electrolyzer, respectively. The energy efficiency of the whole system is the ratio between the useful energy effect of the system and the energy input required to drive it (even if it uses only renewable energy sources). The energy inputs are solar and wind energy and useful outputs are cooling at the evaporator of the absorption chiller, electricity, and produced syngas methane.
2.3. Exergy Balance
Exergy analysis is a powerful tool to identify inefficiencies of industrial processes and to improve them. Exergy comprises thermomechanical and chemical components, and it is the maximum amount of useful work that can be achieved by a system when it evolves up to reach equilibrium with the environment.
The total specific exergy of a stream is expressed as [
48]:
where h and T are enthalpy and absolute temperature, and R
i is the particular gas constant of chemical species i. x
i and y
i denote the mass fraction and mole fraction of chemical species i, ex
chi is the specific chemical exergy of chemical species i. and z, g, and v are height, gravitational acceleration, and velocity, respectively. The subscript i denotes chemical species i, and 0 refers to the environment condition (dead state).
Potential and kinetic exergy changes can be assumed negligible.
Table 3 summarizes the exergy efficiency and the exergy destruction rate (
) for each component of the proposed system [
49,
50,
51,
52,
53,
54].
Where, for wind turbine equations, ρ represents the air density, A2 denotes the swept area of the wind turbine, and u is the wind velocity as mentioned above.
The whole system exergy efficiency can be obtained as:
where subscripts E, T, P, amb, 0 denote evaporator of the chiller, turbine, pumps, ambient, and dead state condition, respectively. The exergy efficiency is defined as the ratio between the useful exergy output from the system and the needed exergy input. Similar to energy efficiency, the inputs of the system are solar and wind energy and outputs are cooling at the evaporator of the absorption chiller, electricity, and produced syngas methane.
2.4. Economic Analysis
Financial analysis can provide a valuable point of view about the capital investment cost, payback period, and the system’s income cash flow. Therefore, this assessment plays a key role to bring an understanding of the financial supports and outcome of the energy system to policymakers, decision-makers, and investors. Each of the following indices is necessary to have a proper economic understanding of a system.
The total investment cost, C
0, is obtained as [
55,
56]:
where subscripts refer to the main subsystems, and K denote the investment cost of each subsystem, which are listed in
Table 4, where T, P, A, and E represent the turbine, pump, surface area of the heat exchanger, and evaporator of an absorption chiller, respectively.
The yearly income cash flow of the proposed system, denoted as CF, is expressed as [
55,
56]:
where Y represents the yearly energy parameter, and k is the specific cost of each of the products, as detailed in
Table 5.
For the investment, the Internal Rate of Return (IRR) is obtained as [
55,
56]:
The Net Present Value (NPV) presents the total investment gain during the lifetime of the project, which can be expressed as [
55,
56]:
where r and N denote discount factor and project lifetime, here considered to be 3% and 25 years, respectively. The Simple Payback Period (SPP) can be obtained as [
55,
56]:
and the Payback Period (PP) equation is [
55,
56]:
As it can be seen, each index is independent of the others and can be taken individually.
Table 3 summarizes the cost of purchase and installation of the system’s components, and
Table 4 summarizes the electricity, cooling, and syngas prices.
2.5. Exergoenvironment Analysis
The exergoenvironment (exergy-environmental) study is a complement to the analysis of an energy system. This analysis clarifies the relationship between exergy destruction and environmental impact and highlights the effect of the system on the environment as caused by the system’s inefficiencies. The smaller the impact factor is, the smaller is its environmental impact, which is achievable by reducing the system’s exergy destruction rate.
The exergoenvironment factor is obtained as [
64,
65,
66]:
where
and
denote, respectively, the overall exergy destruction rate and input of exergy into the system. For an energy system, the effectiveness factor of environmental damage can be evaluated as [
64,
65,
66]:
where
represents the coefficient of exergoenvironmental impact expressed as [
64,
65,
66]:
For any energy system there is an exergoenvironmental impact improvement that illustrates the positive effect of the energy system on the environment, which can be evaluated as [
64,
65,
66]:
The stability factor of exergy can be obtained as [
64,
65,
66]:
3. Result and Discussion
3.1. System Specification
In this section, the results of the modeling that was performed in the MATLAB software are reported and discussed. One main code has been written in MATLAB. Four subroutines are written for water lithium bromide properties calculation, wind turbine energy and exergy analyses, sunrise and sunset time calculation for each day of a year, and Terminol properties calculation. Refprop software was used for R134a properties calculation. The section of the program is shown in
Figure 2.
The proposed system is located in the Tehran province (Iran) that has an annual average of 13 h of daylight per day. The city experiences relative humidity from 64% to 25% during a year. Moreover, the annual rainfall can range from 40.8 mm to 1.1 mm, and the wettest month of the year can have 10 rainy days [
67].
Table 6 summarizes the system’s specifications, and
Table 7 lists the basic parameters of the solar dish collector [
51].
Table 8 includes the wind turbine specifications (model Tuge 10 kW [
61]). The different thermodynamic properties for different points are from the system on 13:00 of 15th of July, which is shown in
Table A2 in
Appendix B.
3.2. Validation of a Model
To the best of the authors’ knowledge, no similar system has been investigated before, and it is not possible to validate the results for the whole system. However, validation can be done for all of the components of the system.
For the solar dish, Equation (A5) is used, and based on the reference [
55] the mean uncertainty is less than 1%.
Ref. [
71] is used for validation of the ORC results. The reported reference for the ORC has the same configuration with this paper, having a heat source temperature of 115
. The power consumption of the pump, the heat exchanging rate in the evaporator and condenser, and power production of the turbine are calculated. The physical properties of R245a are near the R134a and the conditions of both cycles are below the critical point. So, all of the main and important parameters in both cycles are checked and validated. The energy efficiency predicted by the model of the present paper is 10%, which compares well with 9.7% efficiency in [
71]; the mean deviation is lower than 3%.
Ref [
72] is used for validation of the absorption chiller results. In that reference are conducted the energy and exergy analyses of a lithium bromide absorption chiller with 90
generator temperature and 10 kW capacity. The COP calculated with the model is 79%, which compares well with that of 76% reported [
72], the mean deviation being close to 3.7%.
The wind turbine model is validated by comparing the evaluated monthly average output of wind turbines with the power curve given on the manufacturer webpage.
Figure 3 shows the results of that comparison, with a mean deviation of 3.9%.
For validation of the solar radiation,
Table 1 of reference [
73] is considered. In this table, the monthly average of solar radiation recorded in Iran meteorological stations from 2003 to 2010 is presented. The average error is around 3.5%, which is acceptable in engineering calculation [
74].
For modeling the PEM electrolyzer, the ref [
43] is used. This paper mentioned that the error of the model is 1.5% by comparing experimental results. For validation of the methanation plant, the ref [
75] is considered. The deviation of methane production by Equation (4) is 2.5%. In general, by considering all of the uncertainties in various components of the system, the total error for this model is around 3.6%.
3.3. Results of Energy, Exergy Analyses
The metrological data for Tehran are presented in
Appendix B.
Figure 4 shows the monthly averaged useful thermal power gain of the solar dish of the proposed system for one year. As expected, this figure follows the pattern of the monthly direct solar beam in
Figure A2. It is expected a system’s heat gain from solar energy changes from 1000 (in Winter) up to 2100 W (in Summer). According to
Figure 4, the system may experience 52% heat gain reduction during the fall season, the maximum heat gain occurs in June and July, while the minimum heat gain occurs in December.
As can be seen in
Figure 5, the averaged ORC electricity production for each month of a year follows a trend similar to that of the useful heat gain from the solar dish, as the ORC energy exergy source is the solar dish heat gain. The electricity production changes from 10 W up to 170 W during a year, June and December having the maximum and minimum electricity production, respectively.
Fluctuations on the monthly averaged electricity production by the wind turbines, during a year, are presented in
Figure 6. As expected, fluctuations in the wind turbine power generation follow the wind speed fluctuations presented in
Figure A3. The maximum and minimum electricity power production from wind occur in May and September, respectively. The electricity production by the wind turbines ranges from 600 W up to 2700 W, which is considerably higher than the ORC power production.
Figure 7 presents the monthly averaged hydrogen production in the PEM electrolyzer for a year. As mentioned before, since electricity consumption of the PEM electrolyzer is provided mainly by wind turbines, the trend in
Figure 7 is similar to the trend in
Figure A3. It is observed from
Figure 7 that the minimum hydrogen production, of about 170 Nm
3 month
−1, occurs in September. The maximum hydrogen production of about 580 Nm
3 month
−1 occurs in May.
Figure 8 presents the monthly averaged methane production of the methanation plant during a year. This figure follows a similar trend as that of the four previous figures, due to the direct link between the methane production in the methanation plant and the hydrogen production in the electrolyzer. The methane production rate changes from 42 Nm
3 month
−1 (in September) up to 140 Nm
3 month
−1 (in May) during a year.
Figure 9 presents the energy efficiency of ORC, the efficiency of the integration of ORC and absorption chiller, and the energy efficiency of the whole proposed system. As can be seen, the energy efficiency of the ORC system, ranging from 0.8% (in February) up to 3. 9% (in June), is smaller when compared with the other two energy efficiencies. The addition of the absorption chiller unit to the system leads to an increase in its energy performance, adding cooling production to the system using energy recovery from the thermal storage tank. After this integration, the efficiency range of the ORC + absorption chiller combination upgrades from 4.6% (in November and December) up to 12.2% (in February). It must be mentioned that in months with lower ORC energy efficiency, integration of the ORC with absorption chiller can have four or five times increase on the efficiency of the ORC + absorption chiller combination. However, in months with the higher ORC energy efficiency, the integration brings two or three times an increase in the efficiency of the ORC + absorption chiller combination. The third trend in
Figure 9 refers to the energy efficiency of the whole system. As it can be observed, the energy efficiency of the whole system tends to follow a similar trend to that of the wind speed fluctuations, evidencing the major role of the wind turbines on the energy efficiency of the whole system and only a minor role of the solar radiation. The energy efficiency of the whole system changes from 9.1% (in September) up to 24.7% (in May).
Figure 10 presents the exergy efficiency of ORC, the exergy efficiency of the ORC + absorption chiller combination, and the exergy efficiency of the whole proposed system. It is seen that adding absorption chiller and wind turbines increases the exergy efficiency, even with some differences. The exergy efficiency of the ORC changes from 0.8% (in February) to 4.2% (in June). A combination of ORC with an absorption chiller increases the exergy efficiency four times in February, and the slightest increase happens in June. It is to be noted that this ORC + absorption chiller combination leads to an exergy efficiency increase that is not so notorious as the increase in energy efficiency (
Figure 9). On the other hand, the exergy efficiency of the whole system is significantly enhanced because of the dominance of the products of the whole system, over the inputs when wind turbine, PEM electrolyzer, and the methanation plant are added. The exergy efficiency of the whole system changes from 8% (in September) up to 23% (in May). Similar to what happens with the previous figures, the exergy efficiency behavior tends to follow the wind speed trend, also in this case evidencing the strong dependence of the system on the wind energy and exergy.
3.4. Results of Exergoenvironment Analysis
Table 9 shows the exergoenvironment impact factor (f
ei), effectiveness factor of environmental damage (θ
ei), and the stability factor of the exergy (f
es).
This shows ORC, ORC + absorption chiller combination, and the whole proposed system. According to Equation (15), the exergoenvironment impact factor is directly affected by exergy destruction rate and has an inverse relation with input exergy to the system, which implies the fact that the lower this factor, the more acceptable the system. As it can be seen, adding absorption chiller and wind turbine both harm this exergoenvironment impact factor. The factor is less than 0.1 for ORC, which makes it the best system over the other two; integration of ORC and absorption chiller increases this factor to 0.2, which for the whole system this factor reaches the value of 0.7. Therefore, from the exergoenvironment impact factor, this integration is not desirable.
Similar to the exergoenvironment impact factor, the less effective factor of environmental damage, the more favorable the system. According to Equation (16), the difference in the effectiveness factor of environmental damage is that this factor is a function of exergy efficiency too, which has an inverse relation with it. This inverse relation can justify the positive impact of adding a wind turbine to the system due to its significant positive impact on the exergy efficiency of the system. Therefore, the ORC remains the best system over two, with a value of 2 of the effectiveness factor of environmental damage, and the next one is the whole system, which has a value of about 4 for this factor, and the worst case is the integration of ORC and absorption chiller with 6 for this factor.
Similarly, to the effectiveness factors of environmental damage, the case with a lower stability factor of exergy would be favorable. According to Equation (19), this factor is a function of exergy product and exergy destruction of a system. As it can be seen in
Table 9, this factor is about 0.75 for ORC and the whole system, while it is about 0.9 for the unfavorable ORC + absorption chiller combination. Therefore, the proposed system has a desirable stability factor of the exergy.
3.5. Results of Economic Analysis
The results of the economic analysis are listed in
Table 10. As can be seen, the SPP and PP indices for the proposed system are 15.75 and 21.6 years, respectively. Total investment cost of the system and yearly income cash flow denoted respectively as C
0 and CF, are 69,665.4 and 4423.18 US
$. The total investment gains during the lifetime of the project, presented as NPV, is calculated as being 5716.1 US
$, and the IRR of the proposed system is 4%.
4. Conclusions
This article presents a hybrid system based on solar and wind energy for residential applications. The system can produce electricity, heating, cooling, and syngas from captured CO2. Energy, exergy, economic, and exergoenvironmental analyses (4E) are performed for the system to evaluate the performance from different viewpoints and the feasibility of the system. This proposed system can be used in regions with windy and high solar radiation condition to recover the renewable energy resources to produce electricity, syngas, heating, and cooling respectively.
The result of the system assessment can be summarized as follows:
The maximum and minimum electricity production from the ORC system is 170 and 10 W in Jun and December, respectively.
Electricity production from wind turbines ranges from 600 W in September up to 2700 in May.
In the methanation plant, syngas production is maximum in May about 140 Nm3 month−1, which in September experiences its lowest amount about 42 Nm3 month−1. The energy efficiency of the system changes from 24.7% (in May) to 9.1% (in September) during a year. Furthermore, annually, the exergy efficiency of the whole system ranges from 8% (in September) up to 23% (in May).
For those three cases, stability factors of exergy are calculated and compared. This factor for ORC, ORC + absorption chiller combination and the whole system are respectively 0.75, 0.9, 0.75. Therefore, ORC and the whole system are the best cases, and ORC + absorption chiller integration is not favorable.
The simple payback period and the payback period of the system are respectively 15.6 and 21.4 years. The total investment cost of the system and yearly income cash flow are 69,129.54 and 4423.18 US$. The net present value is 5818.13 US$, and the internal rate of return is 4%.