Waste heat recovery (WHR) using conventional technologies can provide appreciable amounts of useful energy from waste heat (WH) sources, thus reducing the overall energy consumption of systems for economic purposes, as well as ameliorating the impact of fossil fuel-based CO2 emissions on the environment. In the literature survey, WHR technologies and techniques, classifications and applications are considered and adequately discussed. The barriers affecting the development and utilization of systems of WHR, as well as possible solutions are presented. Available techniques of WHR are also discussed extensively, with a particular interest in their progressive improvements, prospects, and challenges. The economic viability of various WHR techniques is also taken into account considering their payback period (PBP), especially in the food industry. A novel research area wherein the recovered WH of flue gases from heavy-duty electric generators was utilized for agro-products drying has been identified, which may be useful in the agro-food processing industries. Furthermore, an in-depth discussion on the appropriateness and applicability of WHR technology in the maritime sector is given a prominent touch. In many review works involving WHR, different areas such as WHR sources, methods, technologies, or applications were discussed, albeit not in a comprehensive way touching on all-important aspects of this branch of knowledge. However, in this paper, a more holistic approach is followed. Furthermore, many recently published articles in different areas of WHR have been carefully examined and the recent findings provided are presented in this work. The recovery of waste energy and its utilization is capable of significantly dropping the level of production costs in the industrial sector and harmful emissions to the environment. Some of the benefits derivable from the application of WHR in the industries may include a reduction in energy, capital, and operating costs, which translate to reduced cost of finished products, and the mitigation of environmental degradation through the reduction of the emission of air pollutants and greenhouse gases. Future perspectives on the development and implementation of WHR technologies are presented in the conclusions section.
Energy is very essential to civilizations as it improves human comfort, enhances the political strength of a nation, and supports technological, industrial, and socio-economic development [1]. Energy demand is very high in recent times due to significant growth in population and industrial activities, thus resulting in an appreciable increase in fuel prices. The continuous combustion of fossil fuels to meet this energy demand has continued to cause progressive destruction of the environment through Greenhouse Gas (GHG) emissions. Numerous strides have been made toward minimizing the quantity of heat discarded into the environment, to reduce the carbon footprint and improve process economics [2,3]. To reduce excessive dependence on the use of fossil fuels to attenuate the impact of associated environmental pollutants, Woolley et al. [4] suggested that manufacturers should give priority to both renewable energy systems and WHR technologies. WHR technologies have proven to have great potential to engender sustainable development, hence Oyedepo and Fakeye [1] opined that favourable policies that will encourage their improved utilization should be enacted by relevant regulatory authorities.
It is noteworthy that higher conversions of energy lead to a reduction in both energy costs and environmental degradation globally. According to Jouhara et al. [2], WHR using available techniques provides useful energy sources and reduces overall energy consumption. Jadhao and Thombare [5] reported that the increase in fuel prices is pushing industries and governments to raise the energy efficiency of combustion engines. Hence, the WHR approach is at the front burner, providing a viable option that promotes the gradual decarbonization of society through energy savings. Thus, efforts are made to effectively utilize more of the available heat from WH sources to cushion the effects of the escalating prices of fuels and the problem of environmental degradation due to their unrestrained usage [6,7].
About a third of the energy consumed globally is associated with the industrial sector, with a prediction of about 34% growth by the year 2035 [1,8]. The direct release of flue gases into the environment, not only results in energy waste but also contributes to environmental damage. However, with the emerging findings concerning the methods of exhaust gas WHR to improve the efficiency of engines as well as the use of low carbon emission alternative fuels, the global energy demand on fossil fuels would surely reduce, which will mitigate the impact of global warming [7,9].
There are hotels, resorts, and motels rendering services to tourists and travellers, which are strategically sited in remotely quiet and clean environments such as forests, islands, and coastlines that are far away from the power grids. To keep the guests comfortable, there is a need to meet their usual demands such as the provision of electricity and hot water, and ICEs are mainly used to actualize such [3]. For business owners to reduce operation costs due to excessive fuel consumption and at the same time help to minimize environmental footprint, WHR techniques are a viable option. Furthermore, in modern-day metropolitan areas, many new buildings, especially high-rise ones have been erected to satisfy housing demands arising from expansion in population and business activities, thus resulting in a sharp rise in district heating requirements. Technologies such as combined heat and power (CHP) systems have been employed to provide both electricity and district heating needs. A WH district heating system integrated with a CHP using absorption heat pumps finds application in decreasing the heating energy consumption of available CHP systems. This works by recovering WH of exhaust steam exiting a steam turbine and is capable of increasing the capacity of heat transmission of the primary heating network.
The recovered WH from IC engines has been used predominantly for turbocharging and cabin heating. A conventional air-conditioning system (ACS) of an automobile operates by drawing energy from the engine to drive its compressor, thus resulting in increased consumption of fuel. Research findings have shown that the air conditioning load of the vehicle is the most significant auxiliary load outweighing even other loads such as rolling resistance, aerodynamic drag, or driveline losses. Hence, the fuel economy of a vehicle drops significantly when the engine is subjected to AC compressor loads. One of the ways of actualizing vehicles’ fuel economy is by using a turbo-powered AC compressor, which does not extract engine power directly as it is driven by the waste energy of exhaust gases.
There are numerous WH sources from the industrial sector such as furnaces, kilns, ovens, power plants, ICEs, etc., which account for about 20–50% of the industrial energy input [1]. Different types of cooling and exhaust gas WHR technologies have been innovatively introduced to reduce energy losses and regenerate power by extracting the available exhaust gas WH from various sources. The recovered waste energy may be used to generate electricity, preheat combustion air, augment vehicle propulsion systems, actualize space heating, etc.
The three essential components required in WHR are the WH source, the technique for WHR, and the application of the recovered WH. The identification and evaluation of WH can be a difficult task in terms of its quality and quantity. Therefore, an understanding of the availability of WH and its recoverability offers a great opportunity for the reduction of energy prices and associated impacts on the environment [1]. The method of application in WHR technology on the one hand depends on the WH temperature and the involved economics. The higher the temperature of WH, the better its quality, thus making the WH recovery process more cost-effective. WHR for high-temperature applications considers the recovery of WH at temperatures over 400 °C, which predominantly comes from direct-fired processes [10]. However, the intermediate-range temperature WHR considers temperatures from 100 to 400 °C (mainly associated with combustion units’ exhaust); whereas temperatures below 100 °C are for the low-temperature range, which usually comes from the parts associated with the process units [10]. Many technologies of WHR are available, but there is still huge potential for their application, which is yet to be achieved in industries [7,11]. Examples of WHR technologies are heat exchangers, turbo compounds, direct energy conversion devices, etc. The use of captured WH is considered an emission-free alternative to the use of expensive fuels or electricity, thereby helping to mitigate the impact of excessive pollutants on the environment. Different areas of application of recovered WH from various sources have continued to emerge in the sphere of research and development.
The recovery of WH is an important means of improving energy efficiency which is geared toward the minimization of energy consumption and GHG emission [12]. The origin and gradual development of WHR can be traced to the 19th century. The first adaptation of a combustion engine to extract the WH of exhaust gases was recorded around the 1920s [13]. By this period, the exorbitant prices of coal in comparison to diesel, influenced dealers in the locomotive business to gradually shift to the use of diesel-powered engines with modified exhaust lines to enable the usage of Rankine Cycle (RC) engines for WHR purposes. The recovered heat was used to cause the vaporization of water to produce more power to drive the locomotive. Toom et al. [14], reported that the exhaust WHR unit produced more power in the range of 15–30% which gave a huge advantage to the diesel engine, mainly during the starting of the locomotive which required a high level of torque. Subsequently, a huge setback was suffered by this development as a result of the sharp decline in the prices of coal and diesel. Therefore, the economic advantage to be derived was negligible in having such a locomotive commercialized. According to Legros et al. [13], there were virtually no additional discoveries on WHR after this period until the emergence of the crisis in the price of oil around the early parts of the 1970s necessitating the enactment of the regulation for the Clean Air Act of the United States. This crisis influenced car manufacturing industries to seek ways of reducing the fuel consumption of automobiles, thus provoking more research to be conducted on the Rankine cycle (RC) technology. Research on the use of RCs for WHR was first conducted on trucks. According to Patel et al. [15], an additional 26 kW of mechanical power was achieved at peak conditions wherein a three-stage axial turbine using a mixture of water and trifluoroethanol was coupled mechanically to the shaft of the engine. Around this time, there were no available records in the literature showing research conducted on passenger vehicles [13]. Research studies done on passenger cars started with Oomori et al. [16], where the engine’s cooling system was linked with a scroll expander to produce a Rankine cycle whose working fluid (WF) was R123. This arrangement achieved a 3% reduction in fuel consumption. Furthermore, discarded WH can be harnessed and applied in other processes or used to preheat combustion air or water by considering the option of process integration [17]. The achievement of 5–40% cost-effective energy savings through the recovery of WH by process integration analysis virtually in all industries was reported by Martin et al. [17]. The historical development of WHR is shown in Fig. 1.
This paper considers different techniques of WHR and their applications in various areas such as the food industry, maritime sector, automobiles, etc. The limitations associated with the implementation of WHR systems, as well as possible remedies, are considered. The progressive improvements, prospects, challenges, and economic viability of various technologies of WHR are discussed extensively. A more comprehensive approach to WHR technologies and applications is followed in this paper compared to previous ones. In addition, many recently published articles in different areas of WHR were carefully examined and the recent findings are presented in this work.
The amount of WH available in an exhaust gas depends mainly on its mass flow rate and enthalpy, which is expressed in Eq. (1) [18]:
where, Q˙ex represents the rate at which the exhaust gas waste heat is lost (kJ/s); m˙ex represents the flow rate of the exhaust gas (kg/s); h(t) is the exhaust gas enthalpy as a function of temperature (t); xi is the mass fraction of the exhaust gas species, and hi(t) is the enthalpy of each specie in the exhaust gas as a function of temperature (t).
For the transfer of heat and its recovery to be achieved, the temperature of the WH source must be higher than that of the WH sink. The magnitude of the temperature difference between the heat source and sink, △T is an important determinant of WH quality. Thus, △T influences the rate at which heat is transferred per unit surface area of the recovery unit, which is useful in the selection of the type of WHR technology to be employed for a particular purpose [15,19].
WHR is grouped into four major areas namely, recycling of energy within processes, WHR for other on-site processes, Combined Heat and Power (CHP) installations for the generation of electricity, and systems for district heating [20]. However, each of the areas has some challenges associated with it. Hence, the interest of researchers is to systematically provide cost-effective and environmentally friendly means of achieving optimum WHR from WH sources using different approaches to enhance the output of industries. There are numerous WH sources, of which some fall within the category of Low-Grade Waste Heat (LGWH) such as flue gas, fluctuating cooling water temperature, exhaust steam etc. [21]. In processes in the industry, High-Grade-Waste Heat (HGWH) is reused after recovery either within the industry or across industries. After reuse, the HGWH is reduced to LGWH; and most WHs below 200 °C are usually dumped into the environment unharnessed [22]. LGWH is referred to as liquid or exhaust steam that is below 100 °C, flue gas below 200 °C, as well as other medium/high-temperature waste heats that may not be completely recovered because of heat sources that are scattered and high cost of recovery. Another aspect of the classification of WH considers the temperature of WH as low when it is less than 100 °C; medium, when it is in the range of 100–600°; and high, when it is above 600 °C [20].
Among all the industries such as cement, ceramics, aluminium, chemical, glass, pulp and paper, food and drink industries, etc., the iron and steel industry has been recognized as the largest heat energy consumer, exhibiting the maximum potential for LGWH recovery [20,23]. However, barriers and limitations associated with adopting a particular WHR technology may be categorized as technical, commercial, and delivery. According to Christodoulides et al. [20], the key barriers as reported by the US. Department of Energy [18] are (i) application, constraints that are temperature specific, the process involved, and composition of Waste Heat Stream (WHS) (ii) inaccessibility of certain heat sources and their transportability, and (iii) costs.
Long PBPs, as well as material-oriented constraints, are considered the major barriers to costs; as investors hardly embark on projects that do not show clear and attractive incentives [1,24]. Another major restriction is the waste stream temperature as industrial facilities involving low temperatures hardly need on-site use, in addition to how less developed and very expensive the technologies for low-temperature power generation are presently. Other significant challenges associated with low-temperature waste streams are the problems of extensive fouling and corrosion due to the condensation of liquid and solid components during the cooling of hot streams in the WHR equipment [18]. Furthermore, for high-temperature WHR, the materials that can withstand the high WHS temperature are very costly, thus increasing the system’s overall cost, thus extending the system’s PBP [20]. Nevertheless, in most practical applications, less costly materials are used which results in significant heat losses externally because of the cooling of the WHS by the surrounding air, thus reducing the efficiency of the system.
Another important limitation to the development and implementation of industrial WHR for the generation of power and other industrial processes is the lack of sufficient experience and relevant knowledge on prospecting, design, and operations of different industrial plants with potential WH resources [25].
The use of WH internally improves the energy efficiency of processes in the industry, whereas the use of WHR externally helps to satisfy the energy demand of other utility services and industrial processes, especially those requiring LGWH [21]. Therefore, the main target of WHR should be established, which will help in improving internal heat recovery to maximize the system’s energy efficiency in the main industry, as well as identify the WHR potential for external use, but with a particular interest in the economic benefits achievable.
The possible solutions to the problems associated with the development and application of WHR technologies were considered by Oyedepo and Fakeye [1] as presented below.
Several methods of recovering and applying WH from power plants and industrial processes are available, such as heat transfer between fluids, mechanical or electrical power production, provision of space cooling or heating in facilities, etc. Heat exchangers are very useful in WHR as they cause the transfer of heat from hot flue gases to the air going into the furnace during the processes of combustion. It is worthy of note that whenever the combustion air is preheated by hot flue gases causing it to enter the furnace at a higher temperature, then the amount of heat required to be supplied to the combustion air by the fuel reduces significantly. Many useful technologies of WHR and their applications are considered in this section.
Recuperators are used to recover WH from flue gases within medium to high-temperature ranges, and they find application in melting furnaces, radiant tube burners, afterburners, etc. [18]. They are used as ancillary devices in gas turbines to improve energy efficiency. Gas turbine recuperators employ the WH of flue gases at high temperatures to preheat the mixture of air and fuel going into the combustion chamber. The incorporation of a heat recovery steam generator for further heat extraction from the flue gas in a conventional steam RC has been found to produce about 50% more electrical energy without more input fuel in the combined cycle plant [1]. Recuperators are generally categorized into radiation, convection, or a combination of the two. A different type of recuperator that combines the advantages of both the convective and radiation type recuperators possesses a bigger shelf with smaller tubes while the cold air flows around the shelf as shown in Fig. 2.
The material used in constructing recuperators may be either ceramics or metal. In applications of WHR with temperatures below 1,093 °C, recuperators made of metals are considered, whereas, for temperatures above this, recuperators made of ceramics are used. High-temperature applications operate within the range of 982 and 1,538 °C for the cold and hot sides, respectively [26].
Regenerators are heat exchangers that intermittently store the heat energy from a high-temperature fluid within a thermal storage medium before its transfer to a colder fluid. The design of a furnace regenerator is such that cold and hot air flow alternately via two chambers made of bricks. For high-temperature applications associated with dirty exhausts, regenerative systems are employed. However, the major demerit of regenerators is mainly due to their large size, presupposing higher capital costs when compared to recuperators [26]. A schematic diagram of a furnace regenerator is shown in Fig. 3.
The system comprises two burners containing refractory materials like aluminium oxide. The flue gas is used in heating this material and when completely heated, there is a reversal in the direction of the flue. The airflow is adjusted such that the incoming air for combustion first passes through the hot burner, and thereafter enters the furnace. The two burners alternate periodically, where one extracts heat from the flue gases, while the other transfers heat to the combustion air. Similarly, rotary regenerators referred to as heat wheels (HWs) facilitate the transfer of heat by storing energy and alternating the flow of cold and hot fluids through the system. It uses a porous disc made of a material of high thermal capacity spinning between the two ducts and causing heat exchange between the hot and cold gas ducts. This technology is cost-effective and suitable for gas-to-gas applications. A schematic diagram of a rotary regenerator is shown in Fig. 4.
HWs particularly are very suitable for applications ranging from low to medium-temperature due to the occurrence of thermal stresses in high-temperature applications. High-temperature differences between the cold duct and the hot duct can cause differential expansion that leads to large deformations, thereby compromising the strength and reliability of the duct wheel’s air seals. However, it is interesting to note that in cases where applications of high temperatures are unavoidable, ceramic wheels can be employed as an alternative measure. Another challenge associated with the application of HWs is the difficulty in preventing cross-contamination that may occur between the two gas streams, as there is the possibility of movement of contaminants in the porous material of the wheel [18]. HWs are applied to space heating and processes of air conditioning.
A passive Air Preheater (PAP) is a WHR device in which there is an exchange of heat between two gaseous fluids for applications ranging from low to medium temperatures. The problem of cross-contamination between the two gas streams is not experienced here, therefore, the device finds application in the exhaust of gas turbines, ovens, steam boilers, etc. PAPs are classified into– the Heat Pipe (HP) and the plate-type. The plate type comprises multiple parallel plates, which produce separate channels for both streams of cold and hot gases. The cold and hot fluids flow alternately between the plates, providing a significant heat transfer area. This device has the advantage of being less susceptible to contamination than HWs. But the device is bulkier, more expensive, and more susceptible to the problem of fouling [18]. The other type-heat pipe (HP), as a heat exchanger is an important heat recovery device, which does not experience cross-leakage between the supply air and exhaust gas. HPs have numerous advantages, like the compactness of heat recovery, absence of moving parts, relative economy, small pressure drop associated with the air side, reliability, as well as total separation of cold and hot fluids. The HP among other applications is mostly employed in the recovery of heat from exhaust gases in a furnace stack [27]. Fig. 5 shows the working cycle of the HP preheater.
Jouhara et al. [2] conducted a test on WHR using a Heat Pipe Heat Exchanger (HPHE) in a ceramic kiln (with varying operational conditions) for a period over 27 h; thus, achieving heat recovery in the range of 76–103 kW. The value of the overall heat recovered per annum was 876 MWh, whereas the return on investment for the system was 16 months with an annual savings of 30,000 GBP. The gas-to-water HPHE was installed by Ref. [29] in Ireland to proffer solutions to a problem associated with a dairy factory, although the sulfur content of the exhaust fired from heavy fuel oil was relatively high in sulfur, therefore, not suitable for use due to condensation at the surface and corrosion. The installation of three HP gas-to-water units was carried out, with the achievement of WHR of 488 kW, thus generating savings of about EUR 87,000/yr. with a PBP of 19 months. In the year 2020, the Horizon project developed a standardized flat plate HP for recovering heat from radiant WH sources with smooth application and minimal cases of disruption of the process [20]. The device has the advantage of the capability for two-phase heat transfer. Another advantage is the flexibility for space requirement and heat transfer area minimization, as well as attractive costs.
It is interesting to note that some designs of burners integrate either recuperative or regenerative principles. In comparison to standalone recuperators or regenerative furnaces, these burners are more compact and simpler in terms of design and construction. Their energy efficiency is higher when compared to burners working with ambient air. A standalone recuperative burner as an aspect of its design makes use of heat exchange surfaces. The reason is to enable the body of the burner to recover as much energy as possible from the exhaust gas passing through the body. A standalone regenerative burner allows the passage of exhaust gases through the body of the burner into a refractory media case, operating in pairs in a manner that is similar to a regenerative furnace. Usually, a recuperative burner exhibits a lower heat exchange area, while a regenerative burner exhibits a lower mass than self-sustaining units. Therefore, their ability to recover energy is lower. However, their ease of retrofitting and their associated lower costs make their choice for WHR an attractive one. The schematic diagrams of the principles of regenerative and recuperative burners are shown in Fig. 6a and b, respectively.
Jang et al. [31] carried out a study on a slab-type heating furnace integrated with regenerative burners and recorded a thermal efficiency of 72%. The system achieved fuel savings of 15% compared to the furnace with a conventional burner without a regenerator. Working with a double regenerative radiant tube burner, Zhong et al. [32] concluded that its efficiency was higher than the efficiency of a conventional radiant tube burner. Thus, the regenerative burner achieved a better reduction in the emission of CO2 and NOx. Similarly, Wunning [33] recorded lower exhaust gas emissions using a newly developed gap flow recuperative burner. The burner achieved almost similar efficiency as a regenerative system using a recuperative design. This was done using a larger heat exchanger surface area with a large number of small recuperators.
A finned tube heat exchanger also referred to as an economizer is a device designed for the exchange of heat, and used for applications within low to medium temperatures. It consists of a circular tube to which fins are attached to increase its heat transfer surface area. A finned tube-type heat exchanger captures the WH of flue gases, using it to heat liquid fluids. This device finds application in the production of home hot water, hot process liquid, hot water for process heat, etc. The mode of operation is such that the liquid passing through the tubes is heated by the exhaust gases flowing across the tubes [18].
The Horizon 2020 project also developed the Heat Pipe Condensing Economizer (HPCE), which integrated the advantages of both heat pipes and economizers [20]. According to Christodoulides et al. [20], the potential market for the HPCE is the entire market for industrial and commercial boilers (ignoring their built-in condensing economizers). The suitable areas of application for HPCEs are industrial systems with acidic and dirty exhausts such as petrochemical industries, etc. [20]. Other potential areas of application are the food, cement, glass, and steel industries. It is also pertinent to note that condensing economizers can recover WH in the range of 10–25% more than the noncondensing types, thus making their primary applications fall within expensive primary fuels [20]. It can also find applications in concentrated-type solar collectors and nuclear power plants.
Economizers employed for the boiler system were able to improve the efficiency by about 1% for every 5 °C exhaust gas temperature reduction; thus, showing the possibility of achieving a 5–10% reduction in the system’s fuel consumption within less than two years of PBP [2,34]. The report of another study conducted by Maxxtec [35] revealed that irrespective of the system’s design, a reduction of the flue gas temperature by 140 °C is capable of reducing fuel consumption by 7%. There are several designs of economizers available (coiled tubes, condensing and non-condensing, and finned tube economizers) which are used for different applications [2]. The condensing and non-condensing designs find application in the improvement of the boiler system’s efficiency, while the other designs are employed in flue gas WHR involving large processing facilities and thermal power plants [2]. The finned tube heat exchanger is shown in Fig. 7. Condensation of flue gas moisture takes place on the economizer tubes when the feed water temperature is not sufficiently high which may lead to the absorption of CO2 and SO2 gases, and the eventual formation of an acidic solution that corrodes the tubes. Other challenges associated with economizer tubes are oxygen pitting, caustic embrittlement, due point corrosion and hydrogen attack.
A waste heat boiler (WHB) is a two-pass boiler that is employed in applications ranging from medium to high temperatures. This water tube boiler is used in the production of steam through the exchange of energy between the exhaust gases and the cold water contained in the parallel tubes as depicted in Fig. 8.
Besides, in cases where the WH is enough to generate the required steam output, auxiliary burners or afterburners are made available to actualize the desired objective [36]. The steam produced may be utilized for process heating or power generation. In most applications of recovered WH, the transfer of heat is continuously made to a cold fluid from a hot one. Applications of WHR in industrial processes have a general rule of thumb, which considers hot fluids at temperatures lower than 120 °C as the limit for WHR because of the risk of condensation of liquids that are corrosive [36]. Besides, the incessant rise in the prices of fuels has made it inevitable to consider the recovery of WH from fluids at temperatures below 120 °C for space heating and some low-temperature WH applications.
A heat pump operates by changing the heat flow direction, and mainly works on the Vapour Compression Cycle (VCC) principle. In a VCC, the circulating fluid is separated physically from the WH source and the user (heat to be used in the process) streams and is re-used cyclically. The user properly so called is the heat to be used in the process. A compression heat pump (CHP) as shown in Fig. 9 is employed for space heating if low-temperature energy from water, ambient air, etc. is raised to the temperature of the heating system by doing some work on the fluid with the aid of a compressor.
A heat pump can upgrade WH quality to a value that may be more than two times the energy which is consumed by the device. Chen et al. [37] stated that the recovery of WH using heat pump technology offers a significant reduction in heat pollution to the environment. There is an increase in heat pump applications, especially in industrial processes due to its capability of recovering LGWH and upgrading it for the production of process steam [36]. Heat pumps are also applied in situations where heating and cooling are required simultaneously. Typical cases of this can be found in plastics factories where the cold water leaving a heat pump is used for the cooling of the injection-moulding machine, while the output heat of the heat pump is utilized for office heating. The device is also used for the drying of products, the drying of compressed air, as well as the maintenance of a dry atmosphere for storage purposes.
A significant reduction in demand for industrial WH and high-quality steam can be actualized through the integration of heat pumps. Liew and Walmsley [38] recorded energy cost reductions of 343,859 and 168,829 USD/year using two-stage thermal vapour compression and four-stage mechanical vapour compression systems, respectively. An application of a hybrid (compression/absorption) heat pump using a mixture of water and ammonia as its WF was carried out by Nordtvedt et al. [39] in the food industry. The hybrid pump recovered WH from the refrigeration system at about 50 °C and delivered hot water at 90 °C.
An absorption heat pump (AHP) is another type of heat pump whose technology is different in comparison with a CHP. In an AHP, the electrical compressor is replaced with two components capable of raising the pressure with just 5% of the compressor’s energy under the same operating conditions [40]. The AHP has more applications than the CHP because of its flexible principle of operation and adjustable cycle structure. The AHPs may be classified based on different purposes as type I for increasing the capacity of heating power, and type II -absorption heat transformer (AHT) for raising the temperature of a heat flow [41,42]. According to Ref. [42], LiBr-water and water-ammonia are the main employed working pairs. AHTs are highly suitable for industrial WHR as it has the capability of upgrading the temperature of WH streams while using only a negligible amount of electrical energy and no additional primary energy.
AHTs are of different types, namely single-stage heat transformers (SSHT), double-stage heat transformers (DSHT) and multi-stage heat transformers, such as triple-state heat transformers (TSHT). The SSHT is capable of achieving small temperature increments up to about 50 °C, which is only suitable for cases of small temperature increases as seen in water purification plants [43]. However, the DSHT, which is an advanced type of SSHT is used to achieve more improved temperature increases up to 80 °C, while maintaining the coefficient of performance (COP) of about 0.36 [44]. Essentially, the DSHT is a combination of two SSHTs. To upgrade the gross temperature lift of a DSHT, the concept of a multi-compartment and generation was proposed by Ji and Ishida [45], wherein the absorber of the cold cycle was connected to the hot cycle's evaporator. The use of two and four-compartment absorbers in the hot and cold cycles caused the exergetic coefficient of performance to increase by 6.81%, and the gross temperature lift by 10.7 °C. However, there was a reduction in the cycle’s COP from 31.44% to 29.34% as a result of the improved gross temperature lift.
SSHTs and DSHTs are only able to achieve gross temperature lifts of roughly 50 °C and 80 °C, respectively. However, many applications in the industry require temperatures of heat energy that are more than 200 °C, which cannot be achieved by either SSTHs or DSHTs. A situation such as this requires a more advanced system like the TSHT [46]. A TSHT comprises nine basic units, viz, a generator, an evaporator, a condenser, an absorber, two absorber-evaporators (operating at different temperatures), and three heat exchangers. However, only a scanty number of investigations have been carried out on the TSHTs. Zhuo and Machielsen [47] showed that a TAHT is capable of achieving gross temperature lift values of 145 °C while maintaining a COP of roughly 0.2. The study conducted by Lee and Sherif [48] demonstrated that TAHTs achieved lower COPs and ECOPs but higher gross temperature lifts than both SSHTs and DSHTs.
The data obtained by Cudok et al. [41] from three major manufacturers of AHTs have revealed a reliable perspective on the level of technology of commercial products and operative installations. From the information obtained, there were only 48 installations of AHTs in 42 plants from 1981 to 2019 with a total capacity of approximately 134 MW. Over 74% of the AHTs were installed in Asia, and about 61% of them were applied in the chemical industry. The economic importance in terms of the feasibility of the AHT installation is based mainly on the ability to consume electricity at only about 1% of its capacity.
Many positive case studies have been reported in the literature concerning AHTs in terms of their capability of recycling appreciable amounts of waste energy during operation, but their commercialization has hugely suffered a low level of implementation. The low implementation of AHTs is partly a result of a lack of interest in the energy savings that can be achieved using WHR technologies, in addition to insufficient knowledge of the effects of CO2 emissions, coupled with the problem of inadequacy regarding the number of specialized technical experts to maintain and certify the reliability of AHTs. Other factors such as high equipment capital costs associated with AHTs may be the reason why many investors are not attracted in the least [49]. The general rule of thumb is that if a piece of equipment does not offer significant returns upon investment with attractive payback periods, they are likely not to be considered as an investment target.
Despite the high cost of investment of AHTs (about 1500 $/kW), it has been established that their use for WHR is to a large extent superior to that of a conventional heat pump whose investment cost is approximately 900 $/kW [50].
In all, the economic evaluations available in the literature show that there is hope for the AHT technology market as the return on investment gathered from previous studies on many of the already installed facilities presents an encouraging economic outlook [41].
The Rankine Cycle (RC) is a typical example of an ideal steam-power cycle. It causes the vaporization of a WF subjected to high pressure, and thereafter allows the expansion of the WF in a turbine. The power produced through the expansion process in the turbine drives a generator for electricity production [51]. An RC that uses steam as a WF is applied in many recent power plants. RCs operating on WH capture the WH generated from a given number of industrial processes, especially facilities that use fuel combustion. The generated power can be utilized to produce electricity to run the vehicle’s electrical gadgets or may be used in augmenting the vehicle’s propulsion system [52].
Many of the conventional techniques of WHR are not efficient for converting the LGWH of flue gases to electricity. However, the emergence of the Organic Rankine Cycle (ORC) proved to be a promising one, as the device exhibited great potential for LGWH applications. Among the numerous thermodynamic cycles employed for LGWH conversion to power, the ORC is the most commercially developed for small and large-scale power plants [53]. The ORC uses the steam RC principle, but employs organic WFs with low boiling points instead of steam, for heat recovery from a heat source of lower temperature. The ORC consists of an expansion turbine, a condenser, a pump, and a boiler as shown in Fig. 10.
Furthermore, whenever there is a need for superheat, a superheater is usually provided. It is interesting to note that the ORC has been under extensive study for many years now. And the pronounced attention given to the Rankine bottoming cycle caused some key players in the automotive industry to initiate an investigation of its potential [55]. A given number of researchers have shown how the ORC was used for the achievement of more than 10% fuel consumption reduction in passenger vehicles as well as trucks used for commercial purposes. Vaja and Gambarotta [56] conducted a performance investigation of a stationary Internal Combustion Engine (ICE) with ORC and achieved a 12% increase in efficiency. Mojtaba [57] carried out research on two ORCs of different configurations with the ability to simultaneously recover WH from exhaust gas and coolant of a diesel engine of 12 L capacity. This was aimed at optimizing the process to maximize the production of power and the cycle’s thermal efficiency. Due to its simple design and ability to recover LGWH, the ORC is considered better than the Kalina and steam RCs as well as many other technologies used in WHR [58]. However, the flammability risk associated with the ORC fluids (hydrocarbons) used for high-efficiency heat recovery should necessitate the investigation of new WFs to ensure compliance with established pollution control measures and regulations [58]. Hydrocarbons as WFs for ORCs have explosive characteristics not withstanding their low costs, good environmental compatibility and high efficiency in waste heat recovery. Hence, it is worthwhile to search for working fluids, which are as efficient as hydrocarbon fluids but are not associated with risks of flammability and other disadvantages such as high cost, environmental incompatibility, etc.
The ORC technology was employed by Casci et al. [59] for medium-temperature exhaust gas WHR in a ceramic firing process using a tile-tunnel kiln, in a production plant for ceramics. A heat transfer fluid (thermal oil) was used for transferring heat to the ORC engine. The overall efficiency obtained approached 80%. Using some real data obtained from the cement industry, Ahmed et al. [60] produced and investigated a design for an ORC in a gas turbine for converting the WH of the gas turbine into electricity. It has been reported that the ORC’s effectiveness using R134a as the WF can go up to 93% [20]. For an option of 7000 h/yr operational period, the economic analysis carried out showed maximum and minimum PBPs of 4 and 2.9 yrs, respectively, whereas an operational period of 8000 h/yr, gave the maximum and minimum PBPs of 3.5 and 2.5 yrs, respectively [20]. A comparative thermodynamic study of the Kalina cycle and ORC was carried out by Nemati et al. [61] for a cogeneration system, and the results obtained showed that the ORC required an optimum pressure value that was considerably lower than that of Kalina, thus showing lower materials and sealing costs of the ORC.
In principle, the Kalina Cycle (KC) which is known as reversed absorption cycle, is a modification of the RC [62]. The major difference between the KC and the RC is the fact that it uses a mixture of substances as its WF, instead of a pure fluid such as water. The WF mixture is composed of two or more substances, especially ammonia (NH3) and water (H2O) [53]. KCs can effectively extract low-temperature heat due to the non-isothermal phase change behaviour of the zeotropic mixture of ammonia and water. The WH is utilized in vaporizing a significant portion of the WF with the aid of the Heat Recovery Steam Generator (HRSG) as shown in Fig. 11. Owing to the low temperature of the WH, a separator is placed after the HRSG to separate the steam from the liquid before admission into the turbine. It is noteworthy that the KC has its shortcomings. The HRSG requires a high steam fraction which causes a lower overall coefficient of heat transfer and a larger heat exchange area. Another disadvantage is that the system is prone to corrosion. The air or CO2 which are impurities in liquid NH3 can cause mild steel-stress corrosion cracking. In addition, NH3 is also a substance that is highly corrosive to zinc and copper [63]. Numerous KC designs share some similarities with the RC, with each design having an application that is specific to different sources of heat as experienced in gas to combined cycles or low-temperature geothermal plants [64]. KCs using WH recovered from a steel plant can produce more than 3 MW of power [62]. Mahmoud et al. [65] estimated net output power of 7.35 MW and a PBP of 21 months using a KC with combined WHR in a cement plant. Zhu et al. [66] adopted a cascade utilization of the source of heat using two evaporators in series and recorded 26.4% power recovery efficiency.
The concept of the KC is increasingly being deployed due to its ability to utilize LGWH within the range of 100–200 °C and the zeotropic nature of the WF. However, the RC has been shown to have a better performance for certain temperature ranges of the WH. From the comparative study conducted by Milewski and Krasucki [67], the efficiency of the KC competed with that of the ORC for WH temperature of 200 °C and above.
To obtain an improved output power from the WH source, efforts have been made toward the integration of the Kalina and the ORCs. Oksel and Koc [68] conducted a study on a combined KC and ORC using exhaust gas WH from a CHP engine. The ORC with a heat exchanger was added between the turbine and the condenser of the KC as shown in Fig. 12.
An ammonia-water (NH3–H2O) mixture was used as the WF in the KC while R123 was selected for the ORC. The exhaust gas of the CHP engine was cooled from 450 to 120 °C while converting its energy to electricity in the KC, thus hindering the performance of ORC. The system generated maximum power output of 168.69 and 42.34 kW for the KC and ORC respectively. The combined cycles recorded a thermal efficiency of 26.5% with a PBP of 4.2 years. Similarly, He et al. [69] applied a combined ORC and KC in the WHR of an ICE. The ORC recovered the WH of the high-temperature flue gas and that of the lubricant while the KC recovered the WH of low-temperature cooling water. The system recorded an overall efficiency of 20.83%.
This thermodynamic cycle which is referred to as the Goswami cycle was proposed by Goswami [70]. The device uses a binary mixture to produce power and refrigeration simultaneously in one loop. It integrates an RC with an absorption cooling cycle. According to Vijayaraghavan and Goswami [71], the cycle has the advantages of the production of simultaneous power and cooling effect within a cycle; design flexibility; high efficiency in the conversion of LGWH, and improved resource utilization possibility when compared to separate systems. This device is still in the research stage. The experimental test rig was installed around the late 90s at the University of Florida, USA.
Another important thermodynamic cycle that uses an ammonia-water mixture as a WF is the trilateral flash cycle (TFC). The expansion process of the cycle starts from the saturated liquid state rather than the vapour phase. The heat transfer from a source of WH to the WF (liquid) is done with near-perfect temperature matching by avoiding the boiling part. The NH3–H2O mixture gives a more suitable match with the temperature profiles in the heat sink. A schematic diagram of the TFC is shown in Fig. 13.
In TFCs, the WHR potential depends largely on the efficiency of the two-phase process of expansion [53,72]. The major disadvantage of TFCs is the unavailability of suitable two-phase expanders with high isentropic efficiencies. Hence, the reason TFCs are yet to experience appreciable success. Extensive investigations of this device carried out in the 1970s, reported adiabatic efficiencies in the neighbourhood of 50% for twin screw expanders (Lysholm-type) [53]. Studies have revealed that it is possible to design and construct twin-screw expanders with more than 80% isentropic efficiencies. The performance evaluation conducted on some screw machines shows that two-phase expansion of fluid with an isentropic efficiency of more than 70% is possible [53].
TFCs with the capability of converting LGWH in the range of 70–200 °C into electricity have been developed [20]. The device has shown huge prospects of not only competing favourably with ORCs but also offering the advantage of a higher potential for heat recovery and better output per unit of heat input. TFCs are also capable of extracting heat from thermal energy sources where it is practically difficult for a Carnot cycle to produce power [73]. Results of several experimental investigations have revealed that TFCs exhibit high prospects as a technology to be further developed for LGWH recovery from thermal energy sources whose temperatures are below 100 °C [74]. Literature reports show that operational TFCs are yet to be a reality, for only a few units are available for demonstration.
The supercritical CO2 Rankine Cycle (SCRC) is a thermodynamic power cycle that has shown very high potential for LGWH recovery [75]. The cycle uses carbon dioxide and CO2 (R-744) as a WF. The advantage CO2 enjoys over some other substances is that it is non-toxic, non-flammable, cheap, and non-explosive; and has attractive critical pressure and temperature of 73.8 bar and 31.1 °C, respectively [75,76]. WFs with low critical temperature and pressure have shown the capability of being directly compressed to their supercritical pressures; and through heating, can also be raised to their supercritical state before expansion. Chen [53] reported that the cycle’s heating process does not go through a distinct two-phase region in a similar way that is observed in conventional steam RCs, thereby achieving a thermal match that is better in the boiler with a lower case of irreversibility. An SCRC was suggested by Yamaguchi et al. [76] for electricity production with the use of solar energy. SCRCs use evacuated-type solar collectors to convert CO2 into a high-temperature supercritical state. In Kyoto, Japan, a test rig of the device was developed and subjected to test under typical summer conditions. The test results revealed that the solar energy-powered RC using CO2 as WF operates stably in the trans-critical region, and the time-averaged power production efficiency of 25% was recorded. However, the annual average efficiency for power production in a previous theoretical study was found to be 22% [76]. The dynamic modelling of an SCRC carried out by Olumayegun and Wang [77] showed that the system performs optimally when the turbine’s inlet temperature is varied according to the fluctuation in the source of waste heat.
Oyedepo and Fakeye [1] reported that an SCRC is capable of generating more power and higher efficiency than the ORC. However, the major barrier in its application is the fact that in a multi-phase flow at the trans-critical stage, the WF’s properties are neither clearly gas nor liquid, for which reason, thus lacks good expanders (with multi-phase compatibility) that are not affected by droplets of liquid and attendant erosion problems. CO2 is selected as the WF for SCRC on the grounds of its low critical pressure, thus allowing lower pressures during operation. Other benefits of CO2 are the fact that it is cheap, readily available, non-toxic, stable, and chemically unreactive within the system’s range of operating temperatures [1,78]. However, the barrier associated with the application of SCRC is that CO2 has a low critical temperature (31.1 °C) which is a limitation on the process of condensation. This is because CO2 is required to undergo cooling below 31.1 °C (say 20.8 °C) to condense [1]. However, cooling the CO2 below ambient temperature conditions introduces design complexities concerning the cooling system, thus necessitating the consideration of alternative WFs such as organic ones [78].
WHR from IC engines has been predominantly applied to turbocharging and cabin heating using absorption chillers. Results of the performance evaluation of the device have shown its ability to enhance significantly the performance of the system depending on the part-load of the engine. Hugues et al. [79], stated that the technique could be employed for the refrigeration and air conditioning of vehicles. An experimental study on the adsorption Air-Conditioning System (ACS) installed in an ICE for the cooling of locomotive driver cabins has been carried out. The system uses the working pairs (zeolite-water) for its operation while sourcing energy from the exhaust gas WH of an ICE. Thus, providing continuous refrigeration to the driver’s cabin instead of doing so using an ACS powered by steam compression cycles. The results of the experiments carried out for the cooling of the locomotive driver’s cabin using a single absorber ACS showed that apart from being easy to control, the device is operationally reliable and is simple structurally [80]. An absorption refrigeration unit coupled to a Caterpillar engine is effective in the cooling of the charge air before its ingestion into the cylinder engine as well as in the processes of air conditioning. Reports in the literature show that an absorption combined cycle in a diesel engine with pre-inter cooling has higher thermal efficiency and output power compared to other configurations. However, the report by Talbi et al. [81] showed that the overall efficiency of an inter-cooler is higher than that of a pre-inter-cooling cycle.
Power plants traditionally convert heat energy into mechanical energy for the production of electricity. However, Thermoelectric Generator (TEG) has been developed to directly generate electricity from heat. A sizeable number of thermoelectric devices have been investigated to ascertain their WHR capability in automotive vehicles. TEGs are the most convenient and promising technologies that convert WH into electrical energy, as they do so without degrading the environment or generating noise [82,83]. They are associated with reduced costs of maintenance and operation due to the absence of moving parts. But they have low conversion efficiency which has posed to be a challenge to their globalization [84]. TEGs for the generation of electricity use the n- and p- type dissimilar semiconductor elements due to their ability to increase the output potential of the device [85]. Fig. 14 shows a typical TEG arrangement for electricity generation.
A thermoelectric device that generated about 58 W at peak conditions using FeSi2 elements was developed in the late 80s. However, subsequent studies were conducted on TEGs for passenger car applications. And in the 90s, the results of research carried out showed improvements in the level of power produced as a record of up to 200 W was achieved in passenger cars or about 1 kW for a small truck application [86]. In WHR systems for combustion engines, the difference in temperature applied across the junction of the device comes from the difference between the hot exhaust gas temperature and the cooling fluid temperature. The factor, ZT (figure of merit), which is a dimensionless term is a characteristic constant for the two conductors used in the TEG. ZT and the WH source and sink temperatures (Thot and Tcold), are among the major determinants of the performance of thermoelectric materials [87]. Thermoelectric devices rely on the ZT for electrical performance. Eq. (2) demonstrates this relationship:
where S is the Seebeck coefficient, σ is electrical conductivity, and λ is thermal conductivity. σ is the reciprocal of electrical resistivity (ρ). The conversion efficiency, ηTEM of TEGs is calculated using Eq. (3):
where ηCarnot = Carnot efficiency (i.e., the maximum achievable heat recovery efficiency)
As ηTEM is related to ZT, good thermoelectric materials are expected to present a high value of Seebeck coefficient, low electrical resistivity, as well as low thermal conductivity [88]. Metals exhibit high values of thermal conductivity, low values of electrical resistivity, and low Seebeck coefficients, thus engendering low values of ZT; whereas the highest possible values of ZT are obtained with semiconductor materials. The most employed materials for thermoelectric applications are bismuth telluride, lead telluride, and skutterudite, which provide ZT s close to 1 [88,89]. According to Hussain et al. [90], modern commercial TEGs are incapable of realizing ZT of more than 1, providing the highest realistic efficiency of around 5% for the conversion of WH of exhaust gas in automotive applications. Gunnar [52] shows that an investigation carried out by the Ford Motor Company in 2009 studied the WHR potential of TEGs in gas-electric hybrid vehicles. The results showed that about 2.4% of the waste energy in the exhaust gas could be recovered for a city cycle. And the value increased to 5.7% for the highway cycle, as a result of the higher loads and the temperatures of exhaust gases that occur under these driving conditions. Baker and Shi [91] reported that a study conducted in 2009 by Honda revealed that the use of the system in a 2.0 L gasoline engine would reduce overall fuel consumption by less than 1%, while Stobart et al. [85] predicted yearly fuel-saving potentials of 3.9%–4.7% for a passenger car and up to 7.4% for a transit bus.
Recent research is focused on industrializing new thermoelectric materials with higher values of ZT. One of the main challenges restricting the achievement of materials that exhibit high ZT is the interdependence of S and λ, where an increase in the value of S causes a decrease in the carrier concentration, which in turn decreases the value of λ. Furthermore, the difficulties encountered in lowering heat losses during the evaluation of σ are considered one of the major challenges [88,92]. It is interesting to note that some researchers in recent times carried out the synthetization of some semi-conductor materials (copper selenide and phase-separated PbTe0.7Se0.3), and generated values of ZT > 2 [88,93].
The properties of thermoelectric materials depend on temperature, giving the highest figure of merit under a certain range of temperature. Therefore, to achieve optimum performance, recent researches consider the design and fabrication of thermocouples with materials that are segmented based due to the operating temperature, to withstand the required temperature of the heat source while attaining the highest figure of merit [88,94].
Turbo-compounding is used to extract more work from the exhaust gases, and the extracted work is added to the system output. An additional turbine is positioned downstream of the turbocharger and the exhaust gas expands in the turbine, thus reducing its enthalpy. When multiplied by the turbine’s efficiency, this enthalpy decrease gives the maximum work that can be obtained from the device. The difference between the device and turbochargers is that in turbochargers, the energy recovered is used to power a compressor, while the output energy of turbo-compounds is used directly to augment the propulsion system of a vehicle. However, in some cases, the output of the device is used to drive a generator that produces electricity for the vehicle. Hence, there are two types of turbo-compounds, namely mechanical and electrical turbo-compounds. Fig. 15 shows one possible configuration for a combustion engine with a mechanical turbo-compound. In turbo-compounds for the generation of mechanical energy, the reduction of the output speed of the turbine is achieved using gears for the speed to match the engine’s crankshaft speed. In addition, a fluid coupling is employed ultimately for the separation of the compound turbine from the crankshaft’s torsional vibrations to preserve the turbine and the high-speed gear set from being damaged [95].
Conversely, the electrical turbo compound is not connected to the vehicle’s propulsion system. This is a huge advantage in that their speed can be controlled independently of the engine’s speed, thus avoiding the danger of having to operate the turbine inefficiently under off-design conditions. Turbocompounds find application mostly in aircraft and heavy-duty engines, where they have caused the reduction of fuel consumption by 3–5%, even though the reduction was achieved under varying operating conditions. For low engine loads, turbo compounds may even have a negative impact as they can cause a slight increase in fuel consumption. This happens due to the increase in the exhaust backpressure caused by the turbine, which results in increased pumping losses during the gas exchange in the combustion engine. However, it is pertinent to note that the increased exhaust back pressure helps to improve the rate of Exhaust Gas Recirculation (EGR) for a short-route EGR system. This is because the pressure gradient between the intake and the exhaust manifold increases.
The simulation carried out by Ismail et al. [95] on a diesel engine of 2 L with a series- turbo-compound, revealed that reduction of the brake-specific fuel consumption could be achieved by positioning the turbine behind the turbocharger. This arrangement, nevertheless, increased the backpressure of the engine. Besides, it was shown that a turbo-compounding unit exhibits high potential for power improvement when linked with an EGR valve as the system generated an additional power of about 14 kW in consideration of isentropic expansion [95,96]. Experimental studies were conducted by Ref. [97] on a parallel turbo compound using an IVECO engine (3 L) of two exhaust configurations of which one was with the original Variable Turbine Geometry Turbocharger (VTGT), and the other linked with a new Fixed Geometry Turbocharger (FGT). The VTGT configuration showed promising results at low engine loads; whereas, at high engine loads, the advantages were minimal when compared with the FGT. However, the two systems showed the potential to recover power in the range of 2–2.5% [94]. Wasselin et al. [98] conducted a comparative study on a turbo compound installed in both a turboshaft engine (used for light rotorcraft) and a diesel ICE. The results of the investigation showed that the diesel ICE offered a better potential to reduce both CO2 emissions and fuel consumption for both high and medium loads as well as for long-range missions. The fuel consumption in the range of 25%–50% in comparison to the turboshaft engine was dependent on power requirements [96].
An investigation of the three modes of turbo compounds, namely parallel, series, and electric turbo compounds was carried out by He and Xie [99] using steady-state simulations at varying engine speeds and loads, and at three driving cycles. The results obtained revealed that the electric turbo compound achieved the highest level in both power gain and Brake Specific Fuel Consumption (BSFC) reduction (above 7%) at both high engine speeds and loads for the varying driving cycles; whereas the parallel turbo compound gave the lowest degree in both power gain and BSFC reduction. However, all the turbo compound types performed well at high engine speeds and loads. According to Douadi et al. [100], the addition of turbo generators to automobiles is capable of increasing their efficiency in the range of 3–10%.
Another innovative heat exchange technology designed for effective WHR and reduction of engine emissions is the Protracted-Finned Counter Flow Heat Exchanger (PFCHE). This device was designed, fabricated and investigated experimentally by Ravi and Pachamuthu [101]. The results obtained showed that the PFCHE has a higher capacity to extract waste heat compared to the same heat exchanger without fins. The PFCHE was able to recover 550 W of waste heat when the fin length varied from 0.6 m to 1.0 m, and the number of fins was increased from 6 to 12; whereas it only recovered 335 W of heat in the absence of fins (Ravi and Pachamuthu [101]. The overall results of the PFCHE showed an increase in the heat transfer rate, brake thermal efficiency and heat transfer effectiveness compared to the heat exchanger operating without fins. Ravi et al. [102] applied the PFCHE to internal combustion engines using a water-ethanol mixture as working fluid and achieved improved brake thermal efficiency in the range of 32–39%, and power in the range of 0.35–0.76 kW, when the turbines operated at 1700–4800 rpm, respectively.
A Combined Heating and Power (CHP) system (cogeneration) makes use of a single fuel source for electric power and thermal energy production. This method has been identified as part of the solutions to improve global energy supply as well as ensure minimized GHG emissions. For a topping cycle, fuel is combusted to generate mechanical or electrical power; and the WH from the power generation produces process heat. However, in a bottoming cycle, fuel is burnt to provide process heat, and the resulting WH from the processes is used to generate power. Among all the power plants running on fossil fuel, the Combined Cycle Gas Turbine (CCGT) system working in the mode of combined heat and power (CHP) is considered the most effective means of exploiting the fuel's energetic potential, thus making it the main development directions of future thermal power generation [103,104] The main parts of the CCGT power plant are the gas turbine and the Heat Recovery Steam Generator (HRSG). The HRSG which is an efficient WHR steam boiler (heat exchanger) recovers WH from the gas turbine’s exhaust gases and uses it to raise steam. The steam produced is either used to generate power through a steam turbine or for process heating. The coupling of HRSG with a gas turbine provides a combined cycle system that produces high thermal efficiency and minimal emissions of CO2 [105]. According to Brozičević et al. [106], the efficiency of CHPs could be increased up to 70–85%.
The main components of an HRSG are the evaporator, super-heater, economizer, and drum integrated to meet the operating demands of the system. A schematic representation of the principle of operation of an HRSG is shown in Fig. 16.
According to Ref. [108], the separate production of heat and electricity is not efficient. The efficiency for the production of electricity using IC engines, steam, or gas turbines is in the neighbourhood of 40%, and the processes result in increased GHG emissions [[109], [110], [111]]. In comparison to separate electricity or heat-generating systems, cogeneration is capable of providing energy savings in the range of 15–40% [[112], [113], [114]]. Different sources of energy such as fossil fuels, solar and geothermal heat, biomass, nuclear and electrochemical power can be used in CHP applications [115]. The rising interest in CHP systems is hinged on their ability to offer a cost-effective means of reducing GHG emissions, in addition to their higher flexibility compared to other power generation systems such as single Joule or Rankine Cycles [116,117]. The installation of HRSGs for the recovery of the WH from a gas turbine exhaust gas to generate superheated steam is viable economically with a high return on investment and attractive financial indicators [118]. The major disadvantage of CHP system is large investment costs as the following are required in its setup: (i) Space for the CHP energy centre (ii) A large diameter-heavily insulated metal piping (iii) Costs to administer and sustain the energy centre throughout the life of the equipment, etc. Other disadvantages are: (i) CHP systems are prone to heat losses to the ground (ii) The heat generated during summer periods may go to waste (iii) Combustion in the cities is the main cause of premature deaths due to excessive air pollution, etc.