Evaluating Micro Hydro Power Generation System under Climate Change Scenario in Bayang Catchment, Kabupaten Pesisir Selatan, West Sumatra

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Evaluating Micro Hydro Power Generation System under Climate Change Scenario in Bayang Catchment, Kabupaten Pesisir Selatan, West Sumatra Pinto Anugrah a *, Ahmad Agus Setiawan a, Rachmawan Budiarto a, Sihana a a Dept. of Engineering Physics, Faculty of Engineering, Universitas Gadjah Mada Jln. Grafika No. 2, Yogyakarta 55281, Indonesia Abstract This study investigates the climate change impacts on micro hydro power generation in Bayang catchment, Kabupaten Pesisir Selatan, West Sumatra. There are three micro hydro power systems in operation today, namely Pancuang Taba (40 kw); Muaro Air (30 kw); and Koto Ranah (30 kw). The Water Evaluation and Planning (WEAP) system is applied to simulate hydrological model and micro hydro power projection under different scenarios of greenhouse gas emissions (A2 and B2) from IPCC reports. The model is performed for the 2013 2025 period. Results demonstrate that climate change will reduce micro hydro power production. Changes in power generation vary up to 7.6% under B2 scenario and up to 15.7% under A2 scenario at the last projection year. Keywords: Micro Hydro ; Climate Change ; WEAP ; Pesisir Selatan 1. Introduction Climate change is one of the central issues facing by people nowadays. The Fifth Assessment Reports of the Intergovernmental Panel on Climate Change (IPCC, 2013) concludes that man-made global warming is due mainly to greenhouse gas emissions, especially CO 2 [1]. One of the reason greenhouse gas emissions were increasing is fossil fuels consumption. To reduce fossil fuel consumption, many countries including Indonesia have developed renewable energy technologies such as hydropower. Hydropower systems are at the management nexus of energy supply, water supply, freshwater ecosystems and flood control [2]. In many developing countries, hydropower represents a significant contribution to the electricity generation matrix [3]. In Indonesia, 10.68% of total electricity generate by hydropower system [4]. Small scale hydropower system is called micro hydro, which can generate power up to 100 kw. * Corresponding author. Phone: +62-878-39377714; E-mail address: pinto.anugrah@mail.ugm.ac.id; pinto.anugrah@gmail.com

The impact of global warming is characterized by changes in temperature and precipitation which affected the hydrological system in many rivers. These two changes in hydrological system will influence the water supply to generate electricity using micro hydro power. Clearly, hydropower production is very sensitive to short- and longterm climatic variability [5, 6, 7]. Water Evaluation and Planning (WEAP) software is used to simulate the changes on hydrological system and assess the impact on micro hydro power generation. Case studies have been carried out in Bayang catchment, Pesisir Selatan, West Sumatra Province. The purpose of this research was to evaluate the micro hydro power generation system and to predict the electricity production until year 2025 under climate change impacts. 2. Methodology 2.1. Study Area Bayang River in Kabupaten Pesisir Selatan runs through Kecamatan Bayang Utara and flows into the Indian Ocean. Alongside the river, there are three micro hydro power plants currently operating and producing electricity for 350 households. The micro hydro plants are Pancuang Taba, Muaro Air, and Koto Ranah which have generating capacity 40 kw, 30 kw, and 30 kw respectively. The catchment encompasses a total area of 196 km 2. The locations of the micro hydro power plants are shown in Figure 1. Fig. 1. Locations of micro hydro power plants, image from 76 miles height above sea level; image from 34000 feet height above sea level. (Source: Google Earth)

2.2. Water Evaluation and Planning (WEAP) WEAP was developed by the Stockholm Environment Institute (SEI). WEAP is a unique water resources and planning software where it simulates hydrologic pattern based on climatic inputs such as precipitation, temperature, humidity, and wind speed. WEAP has two primary functions [8, 9]: Simulation of natural hydrological processes (e.g., runoff and infiltration) to enable assessment of the availability of water resources within a catchment; and Simulation of anthropogenic activities superimposed on the natural system to influence water resources and their allocation (e.g., consumptive and non-consumptive water demand) to enable evaluation of the impact of human water use. Prior research has been done using water year method and climate sequences in Bayang catchment. This research was conducted based on historical data on climatology (precipitation, relative humidity, temperature, solar radiation and wind speed). As the result, micro hydro power productions are decreasing in dry season. On the contrary, in wet season, the power productions could not exceed the maximum turbine flow [10]. Following research was modeling hydrological system and micro hydro power generation under climate change condition. The climate change scenario was simulated under the A2 and B2 scenario of IPCC in greenhouse gas emissions [11]. Both scenarios described increasing temperature and decreasing precipitation particularly in Sumatra region. 3. Results and discussion There are three micro hydro power plants which currently operating alongside Bayang River. Each micro hydro generated electricity for one village. All electricity supply to this area is generated by these three micro hydro systems. Approximately 350 households utilize electricity from micro hydro. In addition, the electricity is also used for government buildings and street lighting. Detailed information related to all three micro hydro systems are shown in Table 1. Table 1. Detail of micro hydro power plants. Micro Hydro Coordinate Fixed Head Debit Power Catchment Area Pancuang Taba 1 0 9 16,99 LS / 100 0 39 48,20 BT 11 m 600 liter/s 40 kw 72 km 2 Muaro Air 1 0 8 56,69 LS / 100 0 37 49,90 BT 22 m 300 liter/s 30 kw 90 km 2 Koto Ranah 1 0 9 27 LS / 100 0 37 17,60 BT 15 m 400 liter/s 30 kw 196 km 2

All data related to climate condition were collected from the Department of Public Works, Water Resource Management Agency of West Sumatra Province. There are two climatology stations identified for this research, shown in Table 2. Table 2. Climatology station near Bayang River. Station Coordinate Sub-basin Danau Diatas 01 0 04 40,3 LS / 100 0 46 35,7 BT Bt. Bujanggadang & Bt. Bayanggadang Tarusan 01 0 15 12 LS / 100 0 29 13 BT Bt. Bayangnyalo All data for climate-hydrological measurement were inserted based on the current accounts for the year 1992. WEAP calculated the stream flow using soil moisture method. A GIS-based map was needed to model the basins of each micro hydro. The hydrological model of Bayang catchment in WEAP was shown in Figure 2. Fig. 2. Schematic view of Bayang River on WEAP

As a data validation, WEAP results on monthly stream flow were compared to debit calculation using Mock Method (Mock, 1973). The calculation was applied to three sub-basins as a representation of each micro hydro power plant, using historical data on climatology from year 1992 to 2012. Comparison results proved that WEAP calculation relatively equal to monthly stream flow using Mock Method. Figure 3 showed the comparison between WEAP calculation and Mock Method on monthly stream flow. (c) Fig. 3. Data validation on monthly stream flow: sub-basin Bt. Bujanggadang; sub-basin Bt. Bayanggadang; (c) sub-basin Bt. Bayangnyalo Two different scenarios (A2 & B2) from IPCC reports were conducted to describe climate change condition in Indonesia, particularly in West Sumatra. Climate change in both scenarios define as increasing temperature and decreasing precipitation until year 2100, due to changes in global greenhouse gas emissions. The A2 scenario (low economic growth but high population growth) will cause increasing temperature up to 2.6 0 C and decreasing precipitation up to 40 mm in year 2100. On the other hand, the B2 scenario (mid economic and population growth) will cause increasing temperature up to 2.25 0 C and decreasing precipitation up to 30 mm in year 2100. Temperature and precipitation changes on both scenarios are shown in Figure 4. and Figure 5. respectively.

Fig. 4. Temperature changes in Indonesia: A2 scenario; B2 scenario [11] Fig. 5. Precipitation changes in Indonesia: A2 scenario; B2 scenario [11] Simulation results indicate that electricity generation is decreasing on both scenarios. Power generation in A2 scenario was decreasing more significantly than in B2 scenario. This was due to economic and population growth is more extreme in A2 scenario compared to B2 scenario. Annual power production on A2 and B2 scenario is shown in Table 3. and Table 4. respectively. Table 3. Annual micro hydro power generation in A2 scenario (MWh). 2013 2014 2015 2016 2017 2018 2019 2020 2021 2022 2023 2024 2025 Pancuang Taba 186.6 182.4 177.9 174.6 170.4 164.6 159.4 153.4 147.5 142.9 137.2 130.1 124.8 Muaro Air 207.2 204.9 202.4 199.4 196.4 193.3 190.0 186.7 183.5 180.2 176.1 171.3 167.2 Koto Ranah 262.7 262.7 262.7 262.7 262.7 262.7 262.7 262.7 262.7 262.7 262.7 262.0 261.2 Total 656.5 650.0 643.0 636.7 629.5 620.6 612.1 602.8 593.7 585.8 576.0 563.4 553.2

Table 4. Annual micro hydro power generation in B2 scenario (MWh). 2013 2014 2015 2016 2017 2018 2019 2020 2021 2022 2023 2024 2025 Pancuang Taba 189.3 187.6 185.4 184.2 181.9 179.1 177.3 174.5 171.5 169.5 165.5 161.3 158.3 Muaro Air 209.7 209.7 209.4 208.3 207.1 205.6 203.7 201.7 199.6 197.2 194.9 192.6 190.2 Koto Ranah 262.7 262.7 262.7 262.7 262.7 262.7 262.7 262.7 262.7 262.7 262.7 262.7 262.7 Total 661.7 660.1 657.5 655.2 651.6 647.4 643.6 638.9 633.8 629.4 623.1 616.6 611.1 Based on Table 3, it is known that power production at the end of year projection (2025) is 553.2 MWh and 611.1 MWh under A2 and B2 scenario respectively. Electricity generation is reduced by 15.7% in A2 scenario and 7.6% in B2 scenario. Graphs of each micro hydro power generation annually are shown in Figure 6. Fig. 6. Power generation in: A2 scenario; B2 scenario

As shown in Figure 6, micro hydro Pancuang Taba and Muaro Air are relatively vulnerable compared to Koto Ranah. This was due to the location of each micro hydro. As known from Figure 2, Koto Ranah micro hydro is located more at the downstream of the river. Thus, it has a larger catchment area than the other micro hydro. As a comparison, electricity production of each micro hydro under different climate change scenario is shown in Figure 7 below. 4. Conclusion Fig. 7. Micro hydro power generation under different climate change scenario Simulation result showed that the annual power production of all three micro hydro is decreasing under climate change scenario. Koto Ranah power plant is relatively stable under climate change scenario compared with the other two micro hydro. This finding could be hints for future adaptation within the electricity generation on Kabupaten Pesisir Selatan. On further research, it is recommended to compare the electricity production which has been simulated on this research with the electricity demand on sub-district scale. In addition, it is also recommended to devise greenhouse gases mitigation scenario based on findings in this research. References [1] Stocker, T.F., Qin, D., Plattner, G.-K., Tignor, M., Allen, S.K., Boschung, J., Nauels, A., Xia, Y., Bex V., and Midgley, P.M. (eds.), 2013, Climate change 2013: the physical science basis, contribution of working group I to the fifth assessment report of the intergovernmental panel on climate change. IPCC. [2] Rheinheimer, D.E., Viers, J.H., Sieber, J., Kiparsky, M., Mehta, V.K., and Ligare, S.T. Simulating high elevation hydropower with regional climate warming in the west slope Sierra Nevada. 2013. Journal of Water Resources Planning and Management 2013; doi: 10.1061/(ASCE)WR.1943-5452.0000373 (20 April 2013).

[3] McPhee, J., Rubio-Alvarez, E., Meza, R., Ayala, A., Vargas, X., and Vicuna. S. An approach to estimating hydropower impacts of climate change from a regional perspective. The Proceedings of Watershed Management Conference 2010. Wisconsin, United States, August 23 th - 27 th 2010. p. 13-24. [4] Statistik PLN 2012. ISSN 0852-8179. PT PLN (Persero), 2013. [5] Ospina-Noreña, J.E., Gay García, C., Conde, C., Magaña, V., and Sánchez, G. Vulnerability of water resources in the face of potential climate change: generation of hydroelectric power in Colombia. 2009. Atmósfera, 22(3):229-252. [6] Ospina-Noreña, J.E., Gay García, C., Conde, C., and Sánchez, G. Water availability as a limiting factor and optimization of hydropower generation as an adaptation strategy to climate change in the Sinú-caribe river basin. 2011. Atmósfera, 24(2):203-220. [7] Mehta, V.K., Rheinheimer, D.E., Yates, D., Purkey, D.R., Viers, J.H., Young, C.A., and Mount. J.F. Potential impacts on hydrology and hydropower production under climate warming of the Sierra Nevada. 2011. Journal of Water and Climate Change, 2(1):29-43. [8] Yates, D., Sieber, J., Purkey, D., and Huber-Lee, A. WEAP21: a demand, priority, and preference driven water planning model part 1: model characteristics. 2005. Water International, 30(4), p. 487-500. [9] Yates, D., Sieber, J., Purkey, D., and Huber-Lee, A. WEAP21: a demand, priority, and preference driven water planning model part 2: aiding freshwater ecosystem service evaluation. 2005. Water International, 30(4), p. 501-512. [10] Setiawan, A.A. & Anugrah, P. Assessment of water supply potential to generate electricity as micro hydro power plant in Bayang catchment, West Sumatra. The Proceedings of 8 th SEATUC Symposium. Malaysia. March 4 th -5 th, 2014. ISBN 978-967-12214-1-9; 2014 p. [OS01]1 4. [11] Susandi, A. Bencana perubahan iklim global dan proyeksi perubahan iklim Indonesia, Bandung Institute of Technology, 2006.