Life cycle inventory of green tea production: case of gambung

E3S Web of Conferences 74, 07002 (2018) ICSoLCA 2018 https://doi.org/10.1051/e3sconf/20187407002 Life Cycle Inventory of Green Production: Case of Gambung Tea Joko Waluyo1,*, Muthia Syafika Haq2, Ajeng Arum Sari1, Ary Mauliva Hada Putri1, Muryanto1, Adhi Irianto Mastur2, Teuku Beuna Bardant1, Sugeng Harianto2, Arief Ameir Rahman Setiawan1, Anny Sulaswatty1 and Edi Iswanto Wiloso1 1 Research Center for Chemistry, Indonesian Institute of Sciences (LIPI), Puspiptek, Serpong, Indonesia 2 Research Institute for Tea and Cinchona (PPTK), Gambung, Indonesia Abstract Since long times ago, Indonesia has been known as one of foremost tea producers in the world. However, in recent years the total export contribution of Indonesian tea is declining. High competition and environmental sustainability issues is among the causing factors. Meanwhile, life cycle assessment has gained more attention to measure the potential impact of a product over its stages, from material extraction, production, distribution, consumption and product disposal. In this study, a life cycle inventory analysis has been performed to Indonesian green tea, using case of Gambung’s green tea factory in West Java Province, Indonesia. Data collection and calculations intended to quantify inputs and outputs of green tea production. The analysis itself was done in the basis of literature study and field data collection. The result of such inventory analysis indicates that to produce 3.2 ton of bulk green tea, needs 15 ton of fresh tea leaf, 31 tubes LPG of 50 kg and 2.7 ton wood pellet are needed. This process also produces 54 kg waste of ash wood pellet, 130 kg crushed-burnt leaf, 65 kg residue, and 11.6 ton vapor released. 1. Introduction Tea is being one of the most commonly consumed beverages in the world. It reaches 20.9%[1]. Indonesia has been historically known as one of tea producing countries in the world. According to FAO statistics 2014, Indonesia was the top seven global tea exporting country. Based on plantation statistics data from 2014, Indonesia has a total tea plantation area of 121,034 hectares [2]. Indonesia produced an average of 147,000 tonnes per year with an annual decline of 1.7%. Increased environmental awareness impacts on trade so that information on environmental performance becomes a competitive value added product. At the global level, procedures for stating the potential environmental impact of a product are regulated in the standards of ISO 14021, 14024, and 14025. * Corresponding author: [email protected] © The Authors, published by EDP Sciences. This is an open access article distributed under the terms of the Creative Commons Attribution License 4.0 (http://creativecommons.org/licenses/by/4.0/). E3S Web of Conferences 74, 07002 (2018) ICSoLCA 2018 https://doi.org/10.1051/e3sconf/20187407002 One method that is often used to calculate the potential environmental impact of a product is Life cycle assessment (LCA) (ISO 14040 and 14044: 2006) [3]. Besides being able to be used to state the environmental performance of a particular product, LCA is also used to compare one product with other products. Despite its importance to the economy, tea processing is predicted having contribution to negative environmental impacts, especially on the environment is related to energy and waste generation [4]. Tea factories emit gaseous as particulate pollutants from factory processes and exhaust fumes from boilers, standby generator sets. The environmental impacts of these pollutants. Exhaust fumes release carbon dioxide and nitrous oxides which are greenhouse gases that cause global warming, sulphur dioxide which is responsible for acid rain and particulate matter which affect human health. Tea factories also requires energy intensive. Life Cycle Inventory analysis (LCI) involves in the compilation and quantification of inputs and outputs for a given product system throughout its life cycle (ISO 14040 1998a). It utilizes process material and energy input–output data to characterize the use and emission of materials within and between processes. Identifies and quantifies the environmental loads involved, e.g. the energy and raw materials consumed, the emissions and wastes generated (life cycle inventory). Life Cycle Inventory analysis (LCI) is defined as a phase of Life Cycle Assessment (LCA) involving the compilation and quantification of inputs and outputs for a given product system throughout its life cycle (ISO 14040). The concept of LCI has been adopted for cleaner production as early as the 1960s, and has had broad industrial and academic application in the last decades [5]. 2. Methodology Life cycle inventory (LCI) is the most work intensive and time consuming compared to other phases in an LCA, mainly because of data collection. The data collection can be less time consuming if good databases are available and if the industry is willing to help. Many LCA databases exist and can normally be bought together with LCA software. Data on transport, extraction of raw materials, processing of materials, production of usually used products such as plastic and cardboard, and disposal can normally be found in an LCA database. Data from databases can be used for processes that are not product specific, such as general data on the production of electricity, coal or packaging. For product-specific data, site-specific data are required. The data should include all inputs and outputs from the processes. Inputs are energy (renewable and non-renewable), water, raw materials, etc. Outputs are the products and co-products, and emission such as CO2,CH4,SO2,NOx and CO to air. The ISO 14041 guidelines suggest energy and material flows that do not constitute a significant portion of intermediate or final products need not be included in the life cycle inventory if they have a negligible environmental impact. Thus, the energy, materials, and emissions associated with RTI building are not included in this life cycle inventory. The major efforts for inventory data in this study were done by generating the required data for new case. In this regard, all the input and output materials and energy for each unit were calculated based on the quantity of the products. Therefore, the primary data in this study was obtained by measuring input and output of the tempeh production using some equipment. 2 E3S Web of Conferences 74, 07002 (2018) ICSoLCA 2018 https://doi.org/10.1051/e3sconf/20187407002 Process flow diagrams show how processes of a product system are interconnected through commodity flows. In process flow diagrams, boxes generally represent processes and arrows the commodity flows (Fig.5). Each process is represented as a ratio between a number of inputs and outputs [6]. 3. Results and Discussion Gambung Tea Factory Located in Bandung regency, 176 km from Jakarta which was managed by Research Center for Tea and quinine. Flow diagram of Gambung Green Tea shown in the following figure. Fig. 1. Flow diagram Gambung green tea; input, process, output 3 E3S Web of Conferences 74, 07002 (2018) ICSoLCA 2018 https://doi.org/10.1051/e3sconf/20187407002 Life cycle inventory boundary for this study was gate to gate, only in the processing tea. The processing of green tea can be described as follows; Fresh shoots from the picking are brought to the tea processing factory. The tea is then spread while being aerated with the help of an electric fan to reduce the water content. Furthermore, with the help of the tea conveyor belt, the winding process is carried out using a double cylinder rotary panner tool which is driven using an electric motor. In this process heat is supplied from the burning of wood pellets. The winding process is run at a temperature of less than 100C for a 3 minute process, the water content of this process is 60%. The next process of tea leaves is cooled then a rolling process using a roller is run at room temperature for 20 minutes at a speed of 60 rpm. The tea leaves are then dried using an ECP device which is driven by an electric motor and LPG heater. The process temperature is 130oC for 25 minutes, the yield of tea leaves is about 35% water. Then with the help of tea leaf conveyor belts brought to the sorting process using a rotary shifter with an electric motor drive. After sorting, the following process of tea leaves is the second heating using electricity and LPG heaters. The heating process is carried out for 2 hours using a rotary dryer and 6 hours using ball tea. The moisture content of the tea leaves results from a second drying process of 4%. Bulk tea leaf products are then carried out by bulk packaging using 40 kg size sacks per sack. Process flow diagram as shown in the following figure. For the information, blue letter indicate for energy, red letter indacete for machine or electricity. Fig. 2. Green tea production processes 4 E3S Web of Conferences 74, 07002 (2018) ICSoLCA 2018 https://doi.org/10.1051/e3sconf/20187407002 Based on direct interview and secondary data collected to the Gambung-West Java green tea industry, the mass balance of the tea production process was summarized as follows. Processes 1. Spreading fresh tea leaf Table 1. Mass balance green tea production Input (kg) Output (kg) Fresh tea leaf 15,000 Lead ready to wither vapor 2. Withering Lead ready to wither 14,250 Withered leaf vapor Crushed & burnt leaf 3. cooling 4. roller Withered leaf 10,370 Leaf ready to roll 8,815 6. Sorting 7. drying II Rolled leaf 8,750 Dried leaf 5,250 Tea leaf I dan II 5,250 750 10,370 3,750 130 Leaf ready to roll 8,815 vapor 1,555 Rolled leaf 8,750 Residue (fluff of leaf) 5. drying I 14,250 65 Dried leaf 5,250 vapor 3,500 Tea leaf I 2,625 Tea leaf II 2,625 Bulk tea 3,218 vapor 2,032 Producing 3.2 tons of bulk tea requires 15 tons of fresh shoots and release 11 tons of steam, 0.4 tons of residue and 0.3 tons of crushed tea leaves. The process also requires 31 unit of 50 kg LPG cylinders. 4. Conclusion In this study, inventory analysis has been performed toward green production system, using gate to gate approach. Tea from the plantation entering the production line and processed, resulting bulk of tea. The result of such inventory analysis indicates that to produce 3.2 ton of bulk green tea, needs 15 ton of fresh tea leaf, 31 tubes LPG of 50 kg and 2.7 ton wood pellet are needed. This process also produces 54 kg waste of ash wood pellet, 0.3 ton crushed-burnt leaf, 0.4 ton residue, and 11 ton vapor released. The result of this study can be utilzed to conduct further analysis using life cycle assessment approach, to estimate the potential environmental impact and propose improvement recommendation. 5 E3S Web of Conferences 74, 07002 (2018) ICSoLCA 2018 https://doi.org/10.1051/e3sconf/20187407002 References 1. 2. 3. 4. 5. 6. Fava Neves M., Trombin V.G., Lopes F.F., Kalaki R., Milan P., 2011, The Orange Juce Business: A Brazilian Perspective, Wageningen Academic Publishers FAO (2014). FAOSTAT [Online]. (Accessed November 2018), http://www.FAO.org ISO. 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