Extracted data of inspected cement factory: raw meal under operation.
The cement industry sector is an energy-intensive industrial sector; cement is the most widely used material for construction and modern infrastructure needs. The cement industry is one of the largest consumers of carbon-containing primary energy sources and one of the primary polluters of the environment. Energy consumption represents the largest part of the production cost for cement factories and has a significant influence on product prices. The potential of waste heat utilization of cement production was determined and a recovery potential accounting site wide in demand is defined by the process integration technique. The author has analyzed the energy consumption of a cement factory to obtain minimum energy needs of production and proposed the options to improve energy efficiency by the process integration approach. The authors conclude that the energy consumption of the cement factory can be reduced by 30%. The results help to the cement plant’s profitability and reduce environmental impact of the cement industry as well as sustainability. Given that it is realized in modern society that infrastructural projects lead to a higher level of economy and sustainability for countries, reducing the production cost in the cement industry is a very important problem.
- process integration
- pinch analysis
- energy efficiency
- cement production
- energy targets
- heat exchangers
Nowadays, cement manufacturing is an energy-intensive industry. The energy costs of cement industry are about 40% of the product cost that indicates that this sector is one of the biggest CO2 emitter. The global anthropogenic CO2 emission of cement industry is approximately 5% . The International Energy Agency reported in 2011 that the world cement production was 3635 Mt. with a forecast rising up to 4556 Mt. in 2020, 4991 Mt. in 2030 and 5549 Mt. in 2050 according to scenarios with high demands. In case of the same scenarios, by 2050, the cement manufacturers have to reduce the CO2 emissions by 15%, with a direct decrease of up to 913 Mt. .
Hence, cement manufacturing has to implement more energy reduction to be more environmentally friendly. However, as there is a large amount of CO2 coming from the existing technology, it is important to estimate a renewable energy potential use in the cement production industry or even switch from conventional fuel to a new one with low CO2 emissions.
Due to great significance of the cement industrial sector and high environmental perception  last time, a lot of researches worldwide have shown the energy efficiency improvement of cement factories and pollution reduction. Most of the published researchers investigated the improvement of the cement technology and different varieties for CO2 emission reduction. Pardo et al.  are trying to define the potential of energy efficiency improvement of the EU’s cement sector and CO2 gaseous emission reduction by 2030. Liu et al.  have presented the retrofit and building of new cement factories in China, accounting different technologies. Chen  had defined the advantages of the clinkering process by compact internal burning of carbon inside a cement shaft kiln. This research demonstrated the competitiveness of the proposed measure with the existing one that uses the precalciner kiln process. The work published by Hasanbeigi et al.  points out the CO2 cost curves for the Thailand cement sector. An estimated potential and expenses of CO2 abatement were investigated taking into account the expenses and CO2 abatement for a variety of applications. As presented by Worrell et al. , an in-depth analysis of a US cement industry considering a potential for energy cost and CO2 emission decreasing by the national technologies database was done. It was found that one of the most effective pyro-processing cement manufacturing systems composed of a calciner, several preheaters and the rotary kiln. The data of observed factory for the analysis of the parameters influencing the energy usage of a rotary kiln were utilized in the research by Atmaca and Yumrutas. Their work highlighted that high-energy savings may be obtained by reduction of heat losses with use of insulation, decreasing the outlet gas temperature and heat transfer enhancement. Sheinbaum and Ozawa  have presented the energy demands and CO2 emissions of the cement sector of Mexico, summarizing, that the measures of a fossil fuel, CO2 and other pollutants reduction have to be focused on the use of environmentally friendly energy sources. These assumptions were also concluded by Mikulčić et al. . With the use of real industrial data and combination of kinds and flow rates of alternative energy sources, the work  estimated the ecological impact of cement manufacturing process. It is concluded that the environmental impact of the cement manufacturing process could be lowered if a more energy-saving process of cement manufacturing is utilized along with alternative fuels.
Stefanović et al.  estimated the potential of CO2 emission reduction that may be lowered partly by use of cement with fly ash in the concrete. The research showed that the properties and quality of the new kind of concrete remain the same. Another work by Zervaki et al.  investigated the properties of the cement mortars manufactured by use of sludge water.It was examined that the sludge water, as well as a dry or wet sludge, may be employed in a mortar manufacturing process without remaining its physical properties. As presented by Wang et al. , the exergy approach combining with an organic Rankine cycle (ORC) and Kalina cycle were made to estimate of cogeneration opportunities of a cement factory as well as the calculation of optimal conditions and maximum efficiency. Process integration methods may be used as well to decrease energy use and emissions as were summarized in the work of Professor Seferlis et al. . Presented approaches are based on thermodynamics laws and have different applications in different processing sectors; this issue was reported by Boldyryev and Varbanov . In order to employ the industrial low potential heat and improve a heat utility system of different users and suppliers, a total site integration (TSI) may be employed as shown by Klemeš et al. . Later, a similar approach was developed by different authors. As an example, Chew et al.  expanded the content of a pinch approach of individual process changes to improve a TSI and adapted the plus-minus principle for process modification options to improve process efficiency. Grip et al.  used the mixed-integer linear programming (MILP) approach, exergy analysis and pinch analysis (PA). Experience and results of a multiple approach were presented and considered in literature by many authors. For instance, Baniassadi et al.  represented a technique for an industrial energy system analysis with the use of modified R-curve approach. This methodology estimates the use of the most efficient fuel type for the industrial utility system. Mian et al.  employed the pinch analysis and the process integration approaches for energy optimization of cement manufacturing with primary energy demands of 3600 MJ/t. Authors calculated the thermodynamically and exergy available amount of heat that can be utilized and summarized that the potential of thermal energy reduction is 30%. However, the authors did not propose the retrofit project design nor was the definition of a feasible temperature approach provided. Summarizing the abovementioned, the recent works were rarely supplemented with proper industrial applications of the methodology, especially for the new heat exchanger network (HEN) design and retrofit of existing ones. The analysis and application of different methodologies are usually faced with process features of different industries. In addition, there is a lack of industrial applications of process integration techniques in the cement manufacturing processes owing to its specific process features and process limitations, such as solid particles of process streams, solid-gas and solid-air heat exchange and fast cooling of gaseous streams. Such approaches can be analyzed and subsequently used in appropriate case studies to achieve a real efficiency of the cement manufacturing processes. Thus, this chapter is dedicated to energy efficiency and pathways toward maximization of feasible heat recovery and the concept design of heat exchange system at the particular cement factory.
The energy efficiency potential of a cement factory is estimated. The total energy consumption of the particular cement manufacturing was compared with the benchmark value. Nowadays, considering a best available technology (BAT), the one with the lowest energy consumption of cement production is the rotary kiln use, many cyclone preheaters and the calciner. This technology has energy demands of a cement factory at about 2.93 GJ/t. The same amount is now used for benchmarking point . Present technologies that use the kiln process have total energy consumption at about 3.65 GJ/t of cement. As mentioned, there are still opportunities to reduce the energy consumption of the particular cement factory.
The main goal of this chapter is to identify the potential of feasible energy recovery and to suggest pathways for a new concept design of heat exchange system avoiding the process traps and limitations. The maximum heat recovery of the particular cement manufacturing was obtained, and the updated heat exchange system was proposed. The author concluded that the energy consumption of the particular cement plant may be lowered by 30%. Thus, the features of the cement production process forced a methodology update to suggest feasible retrofit pathways with the objective of achieving the optimal temperature approach of the heat exchange system. There are different streams and processes that contain solid particles, gaseous phase and fast cooling down; these facts make a solution more complicated by the special construction of the process equipment, which causes impossible a heat transfer between some process streams.
2. Description of process flow diagram
Quarrying is the first step of the cement manufacturing (see Figure 1). Inside the quarry that is close to the cement factory, low- and high-grade marl and limestone are mined by blasting. Further, the raw material with granulation of up to 800 mm has to be transported via dump trucks to the hammer crusher, where it is crushed to the granulation of 0–80 mm for marl and 0–50 mm for limestone.
The low-grade and high-grade marl and quartz (silica corrective material) are then stored separately. From the depository the raw materials are transferred to the vertical roller mill with a capacity of 170 t/h and appropriate raw meal is produced. The storage of current raw meal has two silos with a capacity of 2200 t each.
The prepared raw meal from the silos is supplied to the kiln. The kiln has an operation capacity of 90 t/h and upper bound of 110 t/h. A total of 57 t/h of the clinker is produced inside the kiln. For the heating of the raw mill, kiln raw meal, and a coal mill, hot flue gases from the kiln are deployed. Gases exit from a preheating tower with a temperature at about 370°C. Flue gases have be cooled down at the cooling tower because the filter bags cannot operate at the temperature higher than 140°C. The flue gases at the cooling tower are cooled to a temperature of 175°C by 10.5 m3 of cooling water. To further reduce the flue gas temperature from 175 to 105°C, fans are used to pump the ambient air. Flue gases go to the stack after filtration, and further, they are discharged into the environment.
At the kiln outlet side the temperature of the clinker is approximately 1450°C. At this stage, to preserve the clinker mineral structure, that is, its quality, the clinker has to be cooled very quickly to a temperature of approximately 150°C. A large amount of ambient air is introduced through seven clinker cooler fans to achieve the target temperature outlet. The ambient air is heated up to 290°C. After that, a small amount of this air is employed as an additional oxygen source in the kiln and a bigger part is supplied for cement mill heating if it is under operation. The operation mode with disabled cement mill envisages air cooling down before the filter bags. The gas has to be cooled to 105°C prior to the clinker cooler filter bags, after the gas is eliminated to the stack by four rows of four blowers.
The hot gases are needed for the cement grinding process. The hot air is taken to the separator where materials (clinker, limestone/slag and gypsum), pre-grinded on the roller press, are heated to extract moisture and prepare the resulting material for filter bags. They can be delivered from the clinker cooler or, in the case when the kiln does not operate, generated by a hot gas generator (HGG) with use of light oil as a fuel. It is the expensive option but it is used only in several weeks when the kiln overhauls. The consumption of the light oil is about 200 l/h.
A material mixture is kept in a bin with a capacity of 70 t that is supplied by a cement ball mill. Dust and fly ash are supplemented after the ball mill depending on the required kind of cement. The cement is then transferred through a bucket elevator to the next separator. Particles comprise the final product that is supplied to the cement silo.
3. Process integration in cement production
The methodology is grounded on the thermodynamic analysis of the heat energy system by composite curves of process streams. The general issues are based on process integration aspects. The pinch analysis (PA) for optimal process structure synthesis is well illustrated by Klemeš et al. . It provides a solution that is very close to the global optimum in a simply and understandable way. The methodology produces the result of potential savings, capital cost and payback period prior to the flow-sheet design. Often, a super targeting procedure is employed to obtain the optimal temperature approach (ΔTmin) of the heat exchanger network, but in this case, it is difficult due to manufacturing issues. The existing process design presumes a hot meal heating inside the kiln by flue gases that cannot be executed by another stream owing to the technology. Another problem is a hot clinker, which is from the kiln. The clinker must be cooled down rapidly, and that is done by fresh ambient air. The level of technology that is used now has several restrictions for process changes. They have to be taken into account when the retrofit of HEN is made. The methodology stages were updated and are presented later to obtain the more feasible solution of an efficient heat exchanger network design.
3.1. Data extraction by energy expertise execution
An audit expertise of a particular cement factory was conducted to verify energy and mass balances. A measurement of temperatures, flow rates and fuel burning efficiency is accomplished. The composite curves approach and balanced grand composite are employed for the estimation of energy targets, heat recovery and the operation condition of heat transfer equipment, taking into account the cross-pinch heat exchange. Inefficient heat transfer is identified, and process restrictions and forbidden matches between heat transfer equipment are determined.
Considering the next step, the composite curves of cement production are constructed to obtain the energy target and pinch point position of the existing and improved process. At this step, process restrictions are not considered, and only thermodynamically available heat recovery is obtained.
3.3. New concept of heat exchanger network
Based on the previous stages, the heat exchanger network is built taking into account the process restrictions. It is shown that the cross-pinch heat transfer still exists and it cannot be avoided in this production process due to features. Process streams with limitations are not excluded from the considerations to show the actual heat recovery and the real energy efficiency potential of cement manufacturing. The heat exchanger network was built for the range of ΔTmin from 1 to 300°C with step 1°.
3.4. Heat recovery improvement
Based on the previous step, energy targets and pinch point location are defined for different ΔTmin, and maximum heat recovery was found. This procedure determines the heat exchanger network temperature approach, cross-pinch heat transfer and topology heat matches in the heat network.
3.5. Economic analysis
All topologies of heat exchanger network are compared with the base case taking into account operation cost, investment for new networks, operation time, tax rate and other economic prerequisites. Economic results of retrofit execution are defined based on the determination of the reduced total cost of the new design with the use of reduced operating and investment cost .
3.6. Utilization of waste heat in cement production
The next step is performed by the analysis of the waste heat potential in the retrofitted cement production. As was identified by grand composite, there is waste heat utilization potential, and its possibility should be analyzed additionally. The appropriate integration and efficient placement of heat engines is used by grand composite, which shows the available energy, the supply and demand temperatures of heat engines and a heat source. The waste heat utilization that is discarded by cooling capacity, along with attempts to derive energy from low-potential heat sources, has motivated the use of heat engines, for example, by the organic Rankine cycle (ORC)  or utilization of wide site cooling and heating demands .
An additional intermediate stream may utilize the heat from process streams to site heating capacities. This may be steam of different pressure, hot water, thermal oil and so on. The selection of the intermediate utility stream is mainly dependent from its start and target temperatures. The T-H diagram represents a total site sink and source profiles by employing individual ΔTmin specifications of heat transfer between process streams to show the real stream temperatures . Total site targets of heating and cooling, heat engine capacity and produced emissions are considered by Sun et al. . The use of multiple intermediate utilities of heat recovery and modified total site targets is represented by Boldyryev  and methodology advances are discussed. All computations were performed by the HILECT software  applying integrated process design with technological restrictions mentioned earlier.
4. Representative case study
4.1. Data collection and reconciliation
This case study was previously introduced by Boldyryev et al. [29, 30]. The energy expertise of the cement factory was conducted during the summer operation mode. The steady-state devices and portable equipment were used. The historical data of process monitoring were collected and analyzed. There are two operation modes of the particular cement factory. The first one is when the raw mill is under operation and, in this case, the cooling water flowrate at the cooling tower is 3 t/h. A hot gas from the kiln is fed into the raw mill and a raw material is heated. The second operation mode presumes that the raw mill is out of operation. In this case, the cooling water flowrate greatly increases and it is 11 t/h. At the same time, the waste heat with hot gases from the kiln is also increased. There are 18 process streams, which may be included to the heat integration of a particular cement factory. There is a heat recovery of an inspected cement plant and a necessary process heat is provided by the fuel combustion while a cooling capacity is delivered by ambient air that is pumped by air fans. Table 1 has all necessary thermophysical parameters of process streams under analysis.
|№||Name of the stream||Type||Supply temperature (°С)||Target temperature (°С)||Heat capacity flowrate (kW/К)||Heat load (kW)|
|1||Gases to raw mill||Hot||370||105||13.35||3537.42|
|2||Gases from the kiln||Hot||860||380||40.97||19,663.31|
|3||Hot gases to cooling||Hot||370||175||11.68||2276.67|
|4||Gases to coal mill||Hot||370||90||0.73||204.75|
|5||Clinker from the kiln||Hot||1450||60||15.00||20,850.00|
|6||Air after clinker cooling||Hot||290||100||70.28||13,352.75|
|7||Air to cement grinding||Hot||270||105||8.86||1461.60|
|8||Raw material in a raw mill||Cold||25||110||41.62||−3537.42|
|9||Kiln raw material||Cold||105||810||21.44||−15,114.42|
|11||Coal/petcoke to coal mill||Cold||25||90||3.15||−204.75|
|12||Coal dust to kiln||Cold||55||170||1.75||−201.25|
|13||Air to the kiln||Cold||25||170||38.13||−5528.29|
|14||Tires to the kiln||Cold||25||170||0.14||−20.30|
|15||Used oil to kiln||Cold||25||170||0.28||−40.48|
|16||Ambient air for clinker cooling||Cold||25||290||78.68||−20,850.00|
|17||Clinker to cement grinding||Cold||25||105||15.00||−1200.00|
|18||Mineral components grinding||Cold||25||105||3.27||−261.60|
Economic data of utilities were also extracted to be able to execute the economic calculation of the retrofit solution. There are two types of fuel supplied to the kiln: coal and petcoke. Cooling water cools down the exhaust gases before the filter bags; the water is fed by the desalination plant. Another cold utility is electricity, and it is used by the hot air coolers, which emerges from the clinker cooling. Cleaned and cooled air from air filter bags is ejected to the environment. A total of 15.6 MW of low-grade heat is ejected to the atmosphere during raw mill operation; this amount is increased up to 19.4 MW if the raw mill is turned off. All fans and pumps of the cooling tower use the electricity.
The primary fuel that is used for this particular cement factory is coal and petcoke. The coal/petcoke ratio is 40/60%, and the caloric values of the fuel are 25.5 and 33 GJ/t, respectively, for coal and petcoke. The average power supply of the cement plant is 5.8 MW, whereas the minimum power consumption is 1.1 MW and the peak load reaches 10 MW. The reduced price of the hot utility is 75.9 EUR/kWy, and the cold utility is 82.0 EUR/kWy.
4.2. Results and discussion
4.2.1. Existing process analysis
Based on the energy expertise, heat balances and stream table data, the composites of the existing cement factory were constructed considering different operation modes of the raw mill. The composite curves of the existing process are presented in Figure 2.
The composite curves in Figure 2 present the energy requirements of the existing cement factory. The operation mode with the raw mill has a heat recovery of 41,125 kW, whereas the process requires extra heating of 19,397 kW and extra cooling of 20,225 kW. For the operation regime without raw mill it is necessary to have larger utility load as presented in Figure 2. The energy demands increase to 22,923 kW and 24,006 kW for heating and cooling, respectively. At the same time, the heat recovery decreases to 37,599 kW during raw mill operation mode. The minimum temperature approach of the heat exchanger network of the existing process with the raw mill operation is 247°C; without the raw mill operation, it goes up to 308°C. Both these temperature differences are calculated by energy expertise, mass and heat balances and data reconciliation. It should be noted that the minimum temperature approach of the particular process is 1°C due to direct heat transfer in a raw mill or at cement grinding. The raw mill operation mode is under further consideration to get low bound of energy-saving potential. It has to be extended in future by development of the factory operation modes taking into account fluctuations of process parameters and to develop a tool for operators. The significant difference between the thermodynamically grounded (see Figure 2) and real minimum temperature approaches may be additionally explained by cross-pinch heat transfer in the existing heat exchanger network. This is well presented in Figure 3 by composite curves. Arrows show that the heat transfer from hot to cold streams and cross-pinch lines is absent as well as cold utilities are used above the pinch in E-108 (Figure 4).
Grid diagram shown in Figure 4 illustrates the initial heat exchanger network representing the heat transfer between the hot and cold process streams and utilities. The grid diagram illustrates cross-pinch heat transfer; it is a reason of increased utility consumption and lowered efficiency. It is a result of concept design, which was done without the use of optimal heat exchanger network methods and mostly oriented proper product quality.
The process design, which was oriented to obtain a product rather than energy efficiency, reduces opportunities for overall efficiency of plant operation as highlighted in . The overview of heat exchangers placement of the initial plant design is shown in Table 2. The initial cross-pinch transfer is now greater than 20 MW that confirms the low efficiency of the initial design of the heat exchanger network.
|Heat exchanger label||Cross-Pinch heat transfer (kW)|
|Network cross-pinch load||20,224.2|
4.2.2. Maximization of heat recovery considering process limitations
By providing pinch analysis, it is possible to get thermodynamically available energy targets for particular cement production that shows a large energy-saving potential. Eliminating the cross-pinch heat transfer and cold utility use above the pinch, it is possible to decrease energy consumption and heat recovery improvement. Additionally, the minimum temperature approach may be lowered to minimize the energy targets. This is well illustrated in Figure 5 by composite curves position for ΔTmin = 20°C. Energy targets for hot and cold utilities are 4076 and 4904 kW, respectively; the heat recovery is enlarged up to 56,446 kW; the heat recovery improvement in case of maximum saving is 15,321 kW.
However, the cement manufacturing process has different features previously mentioned in Part 3 of this chapter, such as process streams with a mixture of solid-gas and others. These issues make the feasibility of the heat exchanger network retrofit with maximum heat recovery as impossible. Based on this, the heat exchanger network of the cement factory has huge energy efficiency potential, but it is not easy to achieve a profitable solution owing to the process limitation connected to heating and cooling process streams No 5 and No 10.
It is impossible to avoid process restrictions when implementing an integrated solution. There are some process streams that have such technological limits. First one is a hot meal that has to be heated from 810 to 1450°C inside the kiln. It is not possible to heat it in another with particular technology. Another issue that should be analyzed additionally is clinker from the kiln; it has to be cooled down rapidly to 60°C. This is done in the existing process by big fan coolers, and the heat of air is ejected to the environment.
The maximum possible heat recovery of the cement factory taking into account the process restrictions was previously discussed in this chapter. There is an energy target (see right Y-axis, Figure 6) and pinch temperatures (left Y-axis, Figure 6); these indexes depend from the minimum temperature approach of the heat exchanger network. Figure 6 shows energy targets (lines 1 and 2 in Figure 6, right axis Y) of the cement factory, which may be lowered to a process limit that is 50°C. The reduction of ΔTmin below 50°C is useless, as shown in Figure 6, due to its increases in the cross-pinch heat transfer and heat transfer area while the energy consumption remains unchanged. This issue also influences the heat exchanger network topology and reduces the cross-pinch heat transfer. The traditional super targeting procedure  does not take into account the technological restrictions, for example, as for particular cement manufacturing, and does not have a feasible solution. In our case, the minimum of total reduced cost corresponds to ΔTmin = 29°C (see Figure 7). Nonetheless, the design of the retrofit for ΔTmin = 29°C has the same energy targets as one with ΔTmin = 50°C but the heat transfer area is much higher (see Figure 6).
4.2.3. New concept of retrofit design
Based on results presented in Figure 6, the targets of the retrofit design of cement production are taken, including the minimum temperature approach, energy requirements and pinch point position.
The grid diagram shown in Figure 8 is the base concept of a new heat exchanger network of a cement factory with minimized energy consumption. It has additionally installed four heat exchangers with an estimated heat transfer area of 1555.1 m2 and total recovered heat energy of 5790.08 kW. The basic parameters of the new heat exchangers are illustrated in Table 3. The new heat exchanger network is presented in Figure 8, and it is shown that there is still a large cross-pinch transfer of 8850 kW. This issue may be additionally investigated in the future research of new efficient technologies of cement manufacturing. The cross-pinch heat transfer of the proposed heat exchanger network is illustrated in Table 4; there is only one cross-pinch heat exchanger.
|Heat exchanger||Cold stream||Hot stream||Load (kW)||Area (m2)|
|Name||Tin (°C)||Tout (°C)||Name||Tin (°C)||Tout (°C)|
|E-114||Tires to the kiln||25||170||Hot air to coolers||290||275.6||20.30||3.4|
|E-115||Used oil to the kiln||25||170||Hot air to coolers||290||261.2||40.48||6.7|
|E-116||Coal dust to the kiln||55||170||Hot air to coolers||290||242.3||201.30||39.9|
|E-117||Air to the kiln||25||170||Hot air to coolers||290||202.6||5528.00||1505.1|
|Heat exchanger||Cross-pinch heat transfer (kW)|
|Network cross-pinch load||8850.0|
The estimated total investment for new heat exchanger network implementation is 256,079 EUR, accounting the installation cost of E-114 and E-115 as 5000 and 10,000 EUR and 30,000 EUR for E-116 and E-117, respectively. The price of the heat transfer area is 800 EUR per 1 m2, and the nonlinearity price coefficient is 0.87. A new concept design allows reduction of operation cost of 914,401 EUR/year assuming 8200 operation hours per annum. The simple payback period of investments is 3.4 months. By applying the process integration approach, the energy consumption is lowered by 2.56 GJ/t of produced cement, which is 14% less than the existing benchmark level. The developed new concept design of energy-efficient cement manufacturing demonstrates the feasible and profitable solution that could be potentially used for retrofit as well as new factory design.
Making an additional analysis with taking into account site-heating needs and power demands of a cement factory other solutions were also proposed in this chapter. The waste heat potential may be used, for example, for electricity generation with use of Organic Rankine Cycle, which is shown in Figure 9a. The heat sources, in this particular case, are process streams 3 and 6 (for more details see Table 1), and the calculated power generation is 2482 kW.
The estimated investment cost of power generation design is about 3.4 million EUR. The analysis of site demands in winter operation mode identified the other option of waste heat utilization, which is a district heating system. The low-grade heat potential of existing cement factory is given in Figure 9b (see curve 3) and due to this measure it is possible eliminating cold utility while the hot utility remains. In a particular case, the primary cold utility is power for air fans (680 kW), and from the other side, 20,225 kW of site heating demands may be covered by low-grade waste heat. The implementation of winter mode retrofit measures requires an estimated investment cost of 20.3 million EUR. The total saving of both retrofit designs during winter and summer operation modes is 7.648 million EUR. The payback time of combined retrofit for winter and summer operation modes is 3.01 per year assuming the total investment cost of 23.7 million EUR.
4.2.4. Impact and future work
An additional analysis of the energy-saving heat exchange system for cement factory presents a room for improvement in terms of efficient energy use. The grid diagram of the proposed heat exchanger network of the cement plant (Figure 8) has illustrated the ways to use waste heat. The potential of waste heat may be used for power generation by heat engines’ application as demonstrated by Quoilin and Lemort . The heat duty of waste gas is 14,338 kW and the temperature is 200°C or higher (see Figure 8). However, if the plant is operated in the mode without a raw mill, the power generation increases as well. Important points that have to be additionally discussed are the fluctuations of plant operation parameters, solid–gas source streams and installation features of power generator.
Another option of waste heat utilization from integrated cement production is the covering of site heating demands. The district heating system may be potentially supplied by waste heat to fulfill energy demands. The maximum capacity of waste heat that may be used is 14,338 kW as illustrated earlier. However, the technical implementation, including the heat losses and pressure drops, has to be additionally analyzed in details along with the economic issues of the retrofit design as well as energy planning. The results presented in this chapter have a cross-disciplinary impact and additional potential for future development of new cement manufacturing processes. A new design of a heat exchanger network could be a part of an energy-efficient environmentally friendly cement manufacturing process. It reduces fossil fuel consumption, CO2 emission and operation cost of cement factories.
The utilization of low-grade heat for district heating systems could help for planning energy systems. The cement manufacturing process may be also considered as an energy source of district heating systems, additional power generation and so on. Nevertheless, the locations of cement factories have to be additionally analyzed with use of other systematic techniques, for example, based on total site analysis  to find a solution really close to the optimum.
This chapter provides results of research, which identified large energy-saving potential in the cement manufacturing process. Main results may be achieved by improvement of heat recovery, and potential of utility reduction is 30% and 29% for heating and cooling capacity, respectively, which translates to lower primary energy sources. These results were achieved by an updated process integration technique and update of a heat exchanger network. The case study of a particular cement factory was considered and feasible solutions were described that require an investment cost of 256,079 EUR with a payback period of 3.4 months. Besides, the improvement of energy efficiency may be additionally reached by improving the existing process of heat transfer equipment. Low-potential heat utilization covering 43% of power demands of the factory during summer operation mode and utilization of 20,225 kW of waste heat to site-district heating during winter operation are determined.
The use of excess heat may provide a way to reduce the primary energy sources and contribute to global CO2 mitigation. This chapter shows a pathway for energy efficiency, main process restrictions and most feasible solutions for a new concept design of the cement industry. Nevertheless, the technical issues have to be additionally discussed for successful implementation.
This work was supported by the EC and Croatian Ministry of Science Education and Sports project “CARBEN” (NEWFELPRO Grant Agreement No. 39). The author acknowledges Holcim Company for provided data and personally Zoran Mohorovic for help in data extraction and reconciliation. The author acknowledges a SDEWES Centre and the Department of Energy, Power Engineering and Environment, Faculty of Mechanical Engineering and Naval Architecture, University of Zagreb, for administrative support.