Microsoft Word - 164.docx CHEMICAL ENGINEERING TRANSACTIONS VOL. 56, 2017 A publication of The Italian Association of Chemical Engineering Online at www.aidic.it/cet Guest Editors: Jiří Jaromír Klemeš, Peng Yen Liew, W ai Shin Ho, Jeng Shiun Lim Copyright © 2017, AIDIC Serv izi S.r.l., ISBN 978-88-95608-47-1; ISSN 2283-9216 Development of a Model for Benchmarking of Energy Consumption and CO2 Emission in Cold-End of Olefin Plant Nassim Tahouni, M. Hassan Panjeshahi* School of C hemical Engineeri ng, College of Engineeri ng, University of Tehran, Tehran, Iran mhpanj@ut.ac.ir Benchmarking of different process industries, such as petrochemical processes, with respect to energy consumption and CO2 emission, is a fundamental measure while implementing a comprehensive energy plan at the national level. Olefin Plant is one of the process industries that is highly energy intensive and needs to be addressed when looking at petrochemical complexes. In this research, olefin cold-end, which requires heat removal from the process via refrigeration at very low temperatures, has been studied. In sub-ambient processes, shaft work requirement is a dominant factor that causes very high energy cost. A conceptual mathematical model has been developed to facilitate energy benchmarking in olefin cold-end processes. A conceptual model using Pinch analysis is developed to predict energy consumption in refrigeration cycles. To develop the model, the cold-end from five Iranian olefin plants were studied and the effect of different factors such as technology, capacity, feedstock and product types were investigated. The gap between the current level of energy consumption and best practice technology using Pinch analysis was determined. The comparison showed an average potential of 17.7 % reduction in shaft work requirement. Having developed the aforementioned model, there is no need to undertake a full retrofit study for olefin cold-end processes anymore because the model can easily be applied to similar processes and the scope for improvement can be identified. Both time and money associated with extra engineering work can be saved. Application of this model to all olefin’s cold-end processes in Iran showed that there would be 65,838 kW/h potential for energy consumption reduction, which is equivalent to about 382,519 t of CO2 emissions. 1. Introduction Olefin plant is one of the most energy-intensive industries in the petrochemical complexes. Ren et al. (2006) reviewed energy efficiency in conventional steam cracking and innovative olefin technologies and reported up to 20 % savings in the pyrolysis section of naphtha cracking and up to 15 % savings in the compression and separation parts in total. A low-temperature separation system such as the cold-end of olefin plant usually consists of three main systems: separation systems (usually distillation column), heat exchange system (multi- stream plate fin heat exchanger or other exchangers) and refrigeration system. The design of the low- temperature separation system is complicated because an interaction exists among the design of distillation columns, heat exchanger networks and refrigeration cycles (Tahouni et al., 2010). Despite of low thermodynamic efficiency and high operational costs, distillation is still very popular for separation systems. Distillation columns demand high-quality energy via reboiler and then reject lower-quality energy via condenser (Kiss et al., 2012). Numerous studies have been reported on improving the efficiency of distillation columns. There are many factors such as different reflux ratios, working pressure (Castillo and Dhole, 1995), side condensing/reboiling, feed preheating/cooling (Van Der Ham and Kjelstrup, 2011) and heat pumps that affect the column efficiency. Dhole and Linnhoff (1993) developed a methodology based on a combination of thermodynamics and practical aspects of column modifications to provide inputs to engineers on the pre-design targets. Pejpichestakul and Siemanond (2013) performed Column Grand Composite Curve on three columns for ethanol production using ethylene hydration and reduced the energy consumption up to 28 %. Mafi et al. (2009) indicated that the exergetic efficiency of the low-temperature cascade refrigeration system in a typical olefin plant is 30.88 %, showing a high potential for improvements. They provided an exergy analysis for multi-stage cascade low-temperature refrigeration systems used in olefin plants and discussed the reasons DOI: 10.3303/CET1756204 Please cite this article as: Tahouni N., Panjeshahi M.H., 2017, Development of a model for benchmarking of energy consumption and co2 emission in cold-end of olefin plant, Chemical Engineering Transactions, 56, 1219-1224 DOI:10.3303/CET1756204 1219 for deviation from reversible processes. Tirandazi et al. (2011) reported that the exergetic efficiencies of the heat exchanger and expansion sections get the lowest rank among the other compartments of the multi-stage refrigeration cycle used for ethane recovery plant. Fábrega et al. (2010) performed exergy analysis to determine the location and amount of exergy degradation in refrigeration cycles for ethylene and propylene production process and decreased exergy losses by 13 %. Many researchers have applied the benchmarking approach to screen the energy efficiency of different industrial plants. Energy benchmark is a powerful tool that compares or evaluates the energy performance of an industrial plant or process unit against a reference or a plant or process standard (Ke et al., 2013). Experience suggests that the ability to benchmark and evaluate energy efficiency is an essential step for successful implementation of an energy performance improvement system. Saygin et al. (2011) estimated the energy savings potentials in 17 industry sectors by comparing their efficiency with Best Practice Technology (BPT) currently under operation. In this paper, a novel conceptual-mathematical model is developed to facilitate energy benchmarking in olefin cold-end processes. This research focused on the olefin cold-end process, which requires heat removal from the process via refrigeration cycles supplying low-temperature cooling. As in sub-ambient processes, shaft work requirement is a dominant factor that causes a very high energy cost. A conceptual model using pinch analysis is developed to predict energy consumption in refrigeration cycles. The cold-end from five Iranian olefin plants were studied and effect of different factors such as technology, capacity, feed stock and product types were investigated. The gap between the current level of energy consumption and best technology using pinch analysis was determined. Owing to the aforementioned model, there is no need to undertake a full retrofit study for olefin cold-end processes anymore because the model can easily be applied to similar processes and the scope for improvement can be identified. 2. Methodology for Benchmarking There are four factors which affect the energy consumption in olefin plant, which are technology licensor, capacity, feed and product. Technology licensor determines the separation consequences and configuration resulting in different energy consumption criteria. Capacity affects the energy consumption criteria reversely and also as the capacity increases the investments for retrofit project become more economical. T he type of feed determines the severity of cracking process and changes the type of furnace and hot section of olefin plant more than the cold section. The scope of petrochemical plants is to synthesise, crack or purify the feedstocks to produce desirable products. The type of products determines the energy demand in processes. Among distillation towers in olefin plants, only ethylene and propylene separation columns are working below the ambient temperature and these two columns have significantly affect the energy consumption criteria. After determining these effective factors, several plants are selected to investigate the factors’ significance. Data for the scope of this model which include de-ethanizer, de-methanizer, C2-splitter processes and associated ethylene and propylene refrigeration cycles are collected. Commercial simulation software is used to simulate the plants and present all information for the current situation. Energy balance is performed on the plants and energy consumption breakdown is presented to illustrate the effect of column consequences and refrigeration cycle configuration. Specific energy consumptions (SEC) in the refrigeration cycles are the indicators in this paper. The indicators are determined in unified basis for all plants for feasible comparison with other plants and best technology. Two criteria are defined using the following Eqs(1) and (2). SEC1 = Refrigeration Cycle work Total flow to cold section (1) SEC2 = Refrigeration Cycle work Ethylene production capacity (2) Due to the extremely cold temperatures in the processing units of olefin cold-end, which affects the specific economic factors due to costly refrigeration processes, the minimum approach temperature is very small in this section in comparison with the hot section. The significant potential for energy savings in the cold-end of olefin plant is related to refrigeration systems. The new methodology proposed to benchmark energy consumption through cold-end olefin plant using Pinch analysis is presented in Figure 1. Since one of the best technology criteria for grass root design of the heat exchanger networks is minimum temperature approach (∆Tmin), the composite curves (CC) and grand composite curve (GCC) are drawn with ∆Tmin of 2 °C. Exergy grand composite curve (EGCC) is produced by converting the temperature axis in the grand composite curve to the Carnot factor and it is a very helpful tool for estimating the work of refrigeration cycles. The area between the EGCC or GCC and the refrigeration levels is related to the refrigeration cycle work. By choosing proper refrigeration levels (those having minimum distance by core process), exergy loss 1220 can be reduced. In this part, for the new GCC, the duty and level of refrigeration are selected to meet the ∆Tmin in each refrigeration level and minimise the enclosed area. The refrigeration cycle is simulated according to the new loads and refrigeration levels and the shaft work of compressors are also computed assuming constant compressor efficiency. Aforementioned indicators for the benchmarking are determined again after performing Pinch analysis. The gap between the benchmark for BT current situations shows the potential for energy saving. Determine effective factors 1- Licenses 2- Capacity 3- Feed 4- Product Select olefin sites Investigate current situation 1- Collect data 2- Validate data and preform energy balance 3- Benchmark for current situation Gap analysis with BT 1- Determine BT design criteria 2- Draw CC and CGC 3- Energy targeting and cold utility selection 4- Retrofit of refrigeration system (refrigeration levels) 5- Benchmark for BT situation Figure 1: New methodology proposed to benchmark energy consumption using Pinch analysis 3. Case Study Five plants are selected for study in this paper to compare the impact of technology licensor, capacity, feedstock and product type factors. Process flow diagrams for the selected plants are collected and reviewed. Table 1 shows the ethylene conversion and recovery section for the five selected plants. Ethylene conversion for Cases 4 and 5 is higher than the other plants due to their feedstock. Cracked gas outlet stream pressure reached to about 35 bar in five compression stages and then cooled to a sub-ambient temperature prior to entering the cold-end of olefin plant. This high-pressure stream is then cooled gradually to very low temperatures via pressure valves and columns through the separation process. The sequences of the columns change the working pressure and temperature (Figure 2). Each plant has three columns to separate C3+, absorb C2+ and split C2 cut, but the sequences of these three columns are varied for each technology licensor. Linde technology is using two absorber columns in addition to three common columns in other units. Table 1: Ethylene conversion and recovery in 5 selected olefin plants Plant Case 1 Case 2 Case 3 Case 4 Case 5 Technology Licensor Lummus Linde Linde Technip Technip Ethylene conversion (%) 45.16 37.71 57.89 78.90 76.92 Mass flow to cold section (kg/h) 150,989 166,587 362,046 272,221 139,941 Ethylene mass fraction in flow to cold section (%) 45.97 39.64 40.89 51.55 51.19 Liquid ethylene product (kg/h) 0 17,536 37,272 37,879 3,900 Gas ethylene product (kg/h) 68,465 49,551 108,080 88,384 59,869 Ethylene recovery (%) 98.6 98.4 98.2 90.0 89.0 4. Results Cold-end of olefin plants and their associated refrigeration cycles are simulated with commercial simulation software and the results are verified with PFD’s data. Table 2 compares energy consumption and SEC criteria for each case study in the current situation. Two linear equations are developed in Figure 3 showing the relationships between refrigeration cycle work and ethylene production capacity/mass flow to cold section. The results of Case 1 are omitted to develop these equations because this plant uses the Lummus old technology and approximately consumes energy twice other units. This surplus energy consumption is due to the sequence 1221 of separation columns and heat exchanger networks design. Based on the R2 value in Figure 3, Eq(3) is used to model the energy consumption in refrigeration cycles versus ethylene production capacity. Refrigeration cycle work (kW) = 0.3337 ( kW. h kg ) × Ethylene production capacity ( kg h ) + 111.67 (kW) (3) Figure 2: Sequences of distillation columns in five selected plants Table 2: Results for current situation Plant Case 1 Case 2 Case 3 Case 4 Case 5 C3H6 Refrigeration Cycle Energy Consumption (kW) 34,100 10,682 23,129 30,538 16,093 C2H4 Refrigeration Cycle Energy Consumption (kW) 12,763 12,776 25,705 11,380 4,458 Energy Consumption in Refrigeration (kW) 46,863 23,459 48,834 41,917 20,551 Cooling Water Duty 101,508 44,416 85,416 68,686 31,730 SEC1 (kW/kg) 0.310 0.141 0.135 0.154 0.147 SEC2 (kW/kg) 0.684 0.350 0.336 0.332 0.322 Another plant (case 6) which has the highest production capacity in Iran is used to verify the developed Eq(3). Case 6 consumes 56,800 kW shaft work through ethylene and propylene refrigeration cycles and produces 16,982 kg/h ethylene. Table 3 compares the design data with the results obtained using Eq(3). Table 3: Results for current situation Case 6* Design data (kW) Developed equation (kW) Error (%) Shaft work consumption in refrigeration cycle 56,800 56,782 -0.032 The BT benchmark based on pinch analysis is carried out to compare the energy performance of the current plants with plants designed with the best technology criteria. The temperature differences between process streams and refrigeration levels are selected at ∆Tmin = 2 °C to reduce the area between GCC and refrigeration levels indicating the exergy loss in heat exchanger network (T0,HEN) (Panjeshahi et al. 2008). Figure 4 shows the GCC and placement of refrigeration levels for case 3. Cracked Gas Compressor Caustic Wash Tower C1/C2 Separation C2/C3 Separation C2 Hydrogenation C2 Splitter CH4 H2 C3+ C2H4 Product C2H6 Recycle Cracked Gas VHP Linde – Case 3 HP & Condensate C3 Absorber C2 Absorber O v h d . Btm. Btm. Ovhd. Btm. Cracked Gas Compressor Caustic Wash Tower C1/C2 Separation C2/C3 Separation C2 Hydrogenation C2 Splitter CH4 H2 C3+ C2H4 Product C2H6 Recycle Cracked Gas VHP Linde – Case 2 HP & Condensate C3 Absorber C2 Absorber Ovhd. Btm. Ovhd. Btm. fyh Btm. Cracked Gas Compressor Caustic Wash Tower C1/C2 Separation C2/C3 Separation C2 Hydrogenation C2 Splitter CH4H2C3+ C2H4 Product C2H6 Recycle Cracked Gas VHP Technip – Case 4 & 5 HP & Condensate Btm.Ovhd. Btm. Cracked Gas Compressor Caustic Wash Tower C1/C2 Separation C2/C3 Separation C2 Hydrogenation C2 Splitter CH4H2 C3+ C2H4 Product C2H6 Recycle Cracked Gas VHP Lummus – Case 1 HP & Condensate Ovhd. Btm. Btm. H 2 CH 4 C 2 H 4 Production C 2 H 6 Recycle C 2 H 6 Recycle C 2 H 4 Production H 2 CH 4 H 2 CH 4 C 2 H 6 Recycle C 2 H 4 C 2 H 6 C 2 H 4 Production , 1222 Figure 3: Benchmarking refrigeration cycle work in cold section for current situation Figure 4: GCC for BT of cold-end case 3 with ∆Tmin = 2 °C Table 4 compares the energy consumption and SEC criteria for each case study in BT situation. Two linear equations are developed (Figure 5) for BT situation to show the relationships between refrigeration cycle work and ethylene production capacity/mass flow to cold section. Case 1 criteria are reduced to more than others but are still about 1.7 times the other units, which highlights the importance of the sequence of separation. The design of the low temperature separation process is complicated because of the interaction amongst the heat exchanger network, separation process and refrigeration cycles. Eq(4) presents a conceptual-mathematical model which is developed to allow energy benchmarking for BT in olefin cold-end processes. BT − Refrigeration cycle work(kW) = 0.1216 ( kW. h kg ) × Mass flow tocold section ( kg h ) − 414.71 (kW) (4) Table 4: Results for BT situation Plant Case 1 Case 2 Case 3 Case 4 Case 5 CH6 Refrigeration Cycle Energy Consumption (kW) 22,459 7,857 17,381 24,017 12,092 C2H4 Refrigeration Cycle Energy Consumption (kW) 8,097 11,681 25,365 10,207 4,167 Energy Consumption in Refrigeration (kW) 30,556 19,538 42,746 34,224 16,259 Cooling Water Duty 74,916 40,076 79,512 58,762 22,673 SEC1 (kW/kg) 0.202 0.117 0.118 0.126 0.116 SEC2 (kW/kg) 0.446 0.291 0.294 0.271 0.255 -165 -135 -105 -75 -45 -15 15 45 0 10,000 20,000 30,000 40,000 50,000 T e m p e ra tu re ( ◦C ) Heat Flow (kW) Net Cold Net Hot Cold Utility Cold Utility 10,000 20,000 30,000 40,000 50,000 60,000 0 0 100,000 200,000 300,000 400,000 10,000 20,000 30,000 40,000 50,000 60,000 0 0 50,000 100,000 150,000 200,000 1223 Figure 5: Benchmarking refrigeration cycle work in cold section for BT situation 5. Conclusions In this paper, benchmarking of cold-end was implemented for different olefin plants, with respect to energy consumption and CO2 emission. The scope of improvements can be identified through the development of a conceptual-mathematical model for energy performance in existing plants and similar plants with BT (designed based on Pinch technology concepts). Application of this model to all olefin cold-end processes in Iran showed that there would be a 17.7 % potential for reduction of shaft work in refrigeration cycles, which is equivalent to about 382,519 t of CO2 emissions. The proposed model enables the engineers to target energy savings in retrofit projects ahead of numerous calculations. As the model can be applied to a group of similar processes and the scope of enhancement can be identified, both engineering time and money can be saved. Reference Castillo F.J.L. 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