ISSN: 0852-0682. E-ISSN: 2460-3945 Forum Geografi. Vol 29 . December 2015: 187-196 Estimate of Changes. (Hermo. Estimate of Changes in Carbon Stocks Based on Land Cover Changes in the Leuser Ecosystem Area (LEA) Indonesia Dedi Hermon Geography Department and Graduate Program State University of Padang Indonesia Corresponding E-mail: dihermon006@gmail. Abstract This research aimed at designing the model of land cover changes in 1990 and 2014, and estimating carbon stock changes in each land cover in Leuser Ecosystem Area (LEA). The spatial model of land cover changes was analyzed by interpreting Landsat 5 TM imagery in 1990 and Landsat 7 ETM imagery in 2014 with ERDAS 9. and Land Change Modeller (LCM) in Idrisi TerrSet v. The analysis of land area changes . in each land cover from 1990 to 2014 used ERDAS 9. 1 with tools Interpreter (GIS Analysis-Matri. Systematic survey method was employed in order to analyze carbon stocks. The sampling technique was stratified purposive composite sampling which used plot technique. The estimate of tree biomass used allometric equation. The estimate of carbon stocks in each land cover in 1990 was measured based on the total of carbon stocks in 2014 which was conversed with the areas of each land cover in 1990. Spatial model of land cover changes in LEA in 1990-2014 showed the changes of area in each land cover which caused the changes of carbon stocks in each land cover as well. Keywords: Leuser Ecosystem Area. Carbon Stocks. Land Cover Change Abstrak Tujuan penelitian adalah untuk menyusun model perubahan tutupan lahan tahun 1990 dan 2014 serta melakukan estimasi perubahan cadangan karbon pada setiap tutupan lahan di Leuser Ecosystem Area (LEA). Model spasial perubahan tutupan lahan LEA di analisis dengan melakukan interpretasi Citra Landsat 5 TM tahun 1990 dan Citra Landsat 7 ETM tahun 2014 dengan ERDAS 9. 1 dan Land Change Modeller (LCM) dalam Idrisi TerrSet v. Analisis perubahan luas lahan . pada masing-masing tutupan lahan periode tahun 1990-2014 menggunakan ERDAS 9. 1 dengan tools Interpreter (GIS Analysis-Matri. Analisis cadangan karbon menggunakan metode survey secara sistematis dengan teknik pengambilan sampel adalah stratified purposive komposit sampling dengan menggunakan teknik plot. Adapun pendugaan biomassa pohon menggunakan persamaan allometrik. Penghitungan perkiraan cadangan karbon pada masing-masing tutupan lahan pada tahun 1990 adalah berdasarkan hasil perhitungan karbon pada tahun 2014 yang dikonversikan dengan luasan masingmasing tutupan lahan pada tahun 1990. Model spasial perubahan tutupan lahan di Leuser Ecosystem Area (LEA) periode 1990-2014, menunjukan terjadinya perubahan luas . pada masing-masing tutupan lahan, sehingga mengakibatkan terjadinya perubahan cadangan karbon pada masing-masing tutupan lahan. Keywords: Leuser Ecosystem Area. Carbon Stocks. Land Cover Change Introduction Carbon is closely related to land cover changes because the largest carbon stocks are on forest area. Hermon . states that carbon stocks in forest land cover are relatively bigger than any other land covers namely shrub, cultivation, and paddy field. Loss of carbon stock happens if land cover of forest, cultivation, and paddy field are changed into settlements which make the dynamics of carbon stock in each land cover are decreasing year by year. Harun . Kustiawan . Pribadi et al. Hermon . and Hermon . explain that the changes of land cover are mostly triggered by people economic activities and development which then dominate and impose Availble online at http://Journals. id/index. php/fg/article/view/1487 natural areas . to change their function. This condition makes the decreasing of carbon stocks in certain areas which then reduce more carbon stocks every year. Lusiana et al. Hermon . Hermon . and Hermon . elaborate that carbon has much influence on climate change, and can give negative effect to the earth because 20% of greenhouse gasses are caused by deforestation or the change of forest areas into another type of land cover. In 2000, it was estimated that the land use emissions, and the changes of land use in Indonesia was 2, 563 Mt CO2 or equal to 20% of the total emissions of land and forest changes in the These emissions were mostly caused by deforestation and forest degradation. Hermon . explains about the correlation between land cover changes and carbon stocks, and its impact on climate change in Padang. It was explained that the land cover changes of forest, shrubs, cultivation to settlements in Padang from 1985-2011 triggered the increasing of greenhouse gases concentrate especially the increasing amount of CH4. CO2, and N2O. The increasing amount of CO2 was caused by forest logging and burning for becoming settlements or other economic activities. The changes of forest land cover into other types of land cover also happened in Leuser Ecosystem Area (LEA). From 2006 to 2009, there was a decrease of LEA forest area for A 400,00 ha in Southeast Aceh Regency. This decrease indicated that LEA was having damaged because of the conversion of forest land cover to other types of land cover. The changes that occurred from year to year cause the change of carbon stocks (WWF, 2. LEA itself is rainforest areas and national parks which consist of swamps, lowland and upland forests, and mountains which are located in two provinces-Aceh and North Sumatra. Geographically. LEA lies between Laut Tawar Lake in Aceh Province and Toba Lake in North Sumatra Province with 2. 6 million hectares areas which cover Southeast Aceh Regency. Gayo Lues. Central Aceh. Bener Meriah. Aceh Singkil. Kota Subulussalam. Forum Geografi. Vol 29 . December 2015: 187-196 Estimate of Changes. (Hermo. South Aceh. Southwest Aceh. Nagan Raya. West Aceh. Aceh Tamiang. East Eceh. North Aceh. Langkat. Dairi. Karo and Deli Serdang. According to its geomorphological areas. LEA has slopes from flat to very steep ones, with the rainfall between 2500-4000 mm/year. LEA has the biggest biodiversity in Asia, so that it has many ecological functions such as water reserve, climate stabilization, mitigation of erosion and flash floods, prevention of pest outbreaks, and carbon stocks (Forestry Department and IFCA, 2007. WWF, 2015. Hermon 2014b. Hermon, 2014. LEA has significant role for keeping the stability of earth temperature and climate. LEA functions as National Park, and is also determined as Biosphere reserves by UNESCO. Threat of LEA sustainability is the conversion of land to become agricultural land . ultivation and paddy fiel. , plantation, and settlements for people living around LEA. This land conversion will change forest land cover into agricultural and residential land cover in which this condition will directly change the carbon stocks in LEA (TFCA Sumatera, 2. The change of carbon stocks are analyzed based on the change of land cover by combining analysis technique of remote sensing imagery and field survey to measure above ground biomass. The objective is to formulate the spatial model of LEA land cover changes as guidance in estimating carbon stock from 1990 to 2014. Research Method Spatial Model of Land Cover Changes in Leuser Ecosystem Area (LEA) The model of land cover change is analyzed based on Zain . Hermon . Hermon . by interpreting Landsat 5 TM 1990 imagery and Citra Landsat 7 ETM 2014 . ath row 130-. with ERDAS 9. 1 as the analysis tool. The classification of land cover change is analyzed with supervised classification technique for each image which resulted on six temporary patterns of land cover, namely . forest, . cultivation, . Forum Geografi. Vol 29 . December 2015: 187-196 Estimate of Changes. (Hermo. paddy field, . shrub, . plantation, . settlement, and . body of water. Before classifying land cover by using supervised classification technique, separability analysis in the form of quantitative analysis is carried out in order to inform us the evaluation of separated areas in each class as a validation of band combination using ENVI 4. 5 (Hermon. The analysis of land cover change is conducted by using Land Change Modeller (LCM) Idrisi TerrSet v. Meanwhile, the analysis of land area change . in each land cover in 1990 and 2014 is conducted by using ERDAS 9. 1 with tools Interpreter (GIS Analysis-Matri. of undergrowth and litter is measured based on the total dry weight per quadrant . n gr/ m2 and conversed to ton/h. which uses the formula: Total of BK . = BK/BB x total of BB . , in which BK . ry weight, g. and BB . et weight, g. The total of carbon stocks is got from the total of biomass multiplied 46 ( the concentrate of C in organic materials is about 46%) (Hairiah and Rahayu. Hermon, 2012. The estimate of carbon stocks in each land cover in 1990 was based on the estimate of carbon stocks in 2014 which was conversed with the areas of each land cover in 1990 (Hermon, 2012. Result and Discussion The Analysis of Carbon Stock Change in Leuser Ecosystem Area (LEA) The analysis of carbon stock in each land cover is carried out by using Above Ground Biomass (AGB) technique with systemic survey method. Sampling technique used is stratified purposive composite sampling with plot technique (Hairiah and rahayu, 2007. Hermon, 2012. The plot size for taking the sample of trees is 10x10m. meanwhile 1x1 m of plot size which is made in each land cover is used for taking the sample of undergrowth and litter (Hermon, 2012. The samples of trees . talks, branches, twigs, and leave. are taken compositely and analyzed with nondestructive method. meanwhile the samples of undergrowth and litter are analyzed with destructive method. The estimate of tree biomass uses allometric equation (Kattering, 2. with BKis 0. 11 p D2. 62 in which D is the diameter of tree at breast height, c. and p is the density of wood. The biomass Spatial Model of Land Cover Change in Leuser Ecosystem Area (LEA) The analysis using Landat 5 TM imagery in 1990 and Citra Landsat 7 ETM imagery in 2014 resulted on the data of land cover changes for the last 24 years, between 1990 and 2014. Spatial model of land cover change in LEA from 1990 to 2014 can be seen in Picture 1 The spatial model of land cover change in LEA from 1990 to 2014 informed us that land cover for settlements was increasing in 2014 compared to 1990. on the other hand, land cover of forest in 2014 as well as land cover of cultivation, plantation, and shrub was relatively decreasing compared to 1990. The increasing of land cover area for paddy field occurred in 2014 compared to 1990. Baban and Yusof . Amdam . and Antrop . explain that spatial model of land cover change will give the information spatially about all variation of land cover changes. Forum Geografi. Vol 29 . December 2015: 187-196 Estimate of Changes. (Hermo. Figure 1. Spatial Model of Land Cover Change in The Leuser Ecosystem Area (LEA) 1990 and 2014 The variation of land cover changes in LEA in 1990 and 2014 was caused by the activities of people surrounding LEA, such as for enhancing settlements, for new paddy field area, or other economic activities (TFCA. The reduction of forest area and the increasing of settlements in LEA indicate that people activities are no longer controllable in utilizing land cover. The reduction of forest areas can be seen in the area between South Aceh Regency and Southwest Aceh (WWF. Figure 2. Gains and Losses Land Cover Area in The Leuser Ecosystem Area (LEA) in Year Period 1990-2014 Forum Geografi. Vol 29 . December 2015: 187-196 Estimate of Changes. (Hermo. The data reveal that in 1990 the area of forest in LEA was 1,341,322. 1 ha. cultivation was 920,528. 3 ha. settlement was 153,231. 1 ha. the body of water was 1,576. 1 ha. Compared to 2014, there was changes in each land cover in which the area of forest was decreasing into 1,205,576. 2 ha. cultivation was decreasing into 638,331. 1 ha. paddy field was increasing into 247,319. 1 ha. shrub was decreasing into 99,098. 1 ha. plantation was decreasing into 19,333. 2 ha. and settlement was increasing into 388,766. 3 ha. meanwhile, there was no change on the body of water which was 1 ha. Chust et al . conveys that no changes in the body of water in certain period of time indicate that the changes of land cover are mostly oriented on agriculture and new settlements. Furthermore. Hermon . elaborates that land cover changes into agriculture . addy field, cultivatio. and settlements have big influence on the changes and loss of carbon stocks. The decreasing of carbon stocks happen if there is a conversion of land cover of forest to agricultural area, and the loss of carbon stocks happen when land cover of forest, paddy field, and shrub is conversed into settlements Table 1. Land Cover Change in the Leuser Ecosystem Area (LEA) in Year Period 1990-2014 Land Cover . Extensive Changes in Land Cover . Increase Reduce Forest Cultivation Paddy Field Shrub Plantation Settlement Body of Water Total Source: Result of GIS Matrix Analysis of Landsat 5 TM 1990 and Landsat 7 ETM 2014 using ERDAS 9. and LCM Idrisi TerrSet v. In the period of 1990-2014, there were many changes of land cover areas into settlements such as forest areas which became settlements for 98,254. 3 ha, cultivation area becoming settlements for 132,380. 1 ha, paddy field area becoming settlements for 876. 1 ha, shrub area becoming settlements for 578. 5 ha, and the changes of plantation areas becoming residential areas for 3,445. 2 ha. Figure 3. Land Cover Changes into Settlements in The Ecosystem Area (LEA) Period 1990-2014 Forum Geografi. Vol 29 . December 2015: 187-196 Estimate of Changes. (Hermo. Fitzsimmons . Lubowski et al. Ritohardoyo . Hermon . Hermon . explain that land cover changes especially the changes of land cover of forest into settlements will continue to occur and always spatially varied either planned or unplanned. Dahroni . states that settlement will always be a source of problem in human history since the development of settlements will cause the uncontrollable land cover changes, particularly on the changes of land cover of forest into other land covers related to settlements and economic activities. The Estimate of Carbon Stock Changes in Each Land Cover \in Leuser Ecosystem Area (LEA) The changes of forest, cultivation, paddy field, shrub, and plantation areas into settlements in LEA from 1990 to 2014 indicated the change of carbon stocks in LEA. For more detail, it is shown in Table 2 below. Table 2. Biomass and Carbon Stocks in the Leuser Ecosystem Area (LEA) in 2014 Land Cover Trees Number/ Tree Biomass g/m ) . on/h. Forest 365,22 Cultivation 15,77 Paddy Field 0,00 Shrub 2,87 Plantation 64,84 Settlement* --Body of Water* --Total 448,70 Source: Data Analysis Research, 2015 652,20 157,70 0,00 28,70 648,40 --4487,00 Litter Biomass on/ . g/m. 18,320 183,20 15,44 154,40 19,89 198,90 26,93 269,30 7,11 71,10 ----87,69 876,90 Total Biomass . on/h. Carbon . on/h. 835,40 312,10 198,90 298,00 719,50 --5. 363,90 764,28 146,56 91,26 137,08 330,97 --2. 470,15 Based on the condition in 2014, the carbon 137. 08 ton/ha, and plantation for 330. 97 ton/ stocks per hectare in LEA was 2,470. 15 ton/ ha. The total of carbon stocks in 2014 in LEA ha which spread on forest area for 1,764. ton/ha, paddy field for 91. 26 ton/ha, shrub for is presented in Table 3 below. Table 3. Total Carbon Stocks in The Leuser Ecosystem Area (LEA) 2014 Land Cover Area . Forest Cultivation Paddy Field Shrub Plantation Settlement* Body of Water* Total Source: Data Analysis Research, 2015 * Not Analyzed Carbon Stocks . on/h. 764,28 146,56 91,26 137,08 330,97 --2. 470,15 In 2014, the total of carbon stocks in LEA was 2,263,081,209. 24 ton which spread on forest area for 2,126,973,801. 70 ton, cultivation for 93,553,806. 01 ton, paddy field for 22,570,359. 31 ton, shrub for 13,584,367. Total Carbon Stocks . 801,70 806,01 359,31 367,54 874,68 --2. 209,24 ton, and plantation 6,398,874. 68 ton. The biggest carbon stocks were in the forest so that the preservation of forest area must be The conversion result of carbon stocks in LEA in 1990 can be seen in Table 4. Forum Geografi. Vol 29 . December 2015: 187-196 Estimate of Changes. (Hermo. Table 4. Prediction of Total Carbon Stocks in the Leuser Ecosystem Area (LEA) 1990 Land Cover Area . Forest Cultivation Paddy Field Shrub Plantation Settlement* Body of Water* Total Source: Data Analysis Research, 2015 * Not Analyzed Carbon Stocks Prediction . on/h. 764,28 146,56 91,26 137,08 330,97 --2. 470,15 Based on the conversion result of carbon stocks, it was known that the carbon stocks in LEA in 1990 were 2,532,550,762. In details, forest areas had the carbon stocks for 2,366,468,283. 87 ton, cultivation for 134,912,686. 27 ton, paddy field for Prediction of Total carbon Stocks . 283,87 686,27 252,38 102,13 437,48 --2. 762,13 1,744,252. 38 ton, shrub for 17,625,102. ton, and plantation for 11,800,437. 48 ton. the period of 1990-2014, there was decrease and increase of carbon stocks on each land cover, as shown in Table 5. Table 5. Decrease and Increase Carbon Stocks on Each Land Cover in the Leuser Ecosystem Area (LEA) Period 1990-2014 Land Cover Prediction of Total Area . Area . Carbon Stocks . on/ Total Carbon Stocks . Decrease in Increse Carbon Stocks Carbon Stocks . Forest 322,1 2. 283,87 1. 576,1 2. 801,70 239. 482,17 Cultivation 686,27 806,01 880,26 Paddy Field 252,38 359,31 106,93 Shrub 102,13 367,54 734,59 Plantation 437,48 874,68 562,80 Settlement* Body of Water* Total 762,13 209,24 290. 659,82 20. 106,93 Source: Data Analysis Research, 2015 * Not Analyzed The decrease of carbon stocks in LEA in 1990-2014 occurred in forest land cover . ,494,482. 17 to. , cultivation . ,358,880. , shrub . ,040,734. 59 to. , and plantation . ,401,562. 80 to. On the contrary, the increase of carbon stocks occurred in land cover of paddy field . ,826,106. because land cover of paddy field was increasing in 2014 for 228,206. 1 ha. The loss of carbon stocks in LEA because of the changes of land cover into settlements from 1990 to 2014 was quite big. it was 194,049,235. 370 ton. details, the loss of carbon stocks because of land cover changes into settlements can be seen in Table 6. Forum Geografi. Vol 29 . December 2015: 187-196 Estimate of Changes. (Hermo. Table 6. Loss of Carbon Stocks in Leuser Ecosystem Area (LEA) because of Land Cover Changes into Settlements Land Cover Change Area . Losses of Carbon Stocks . 1 Forest-Settlement 096,404 2 Cultivation-Settlement 627,456 3 Paddy Field-Settlement 952,886 4 Shrub-Settlement 300,780 5 Plantation-Settlement 257,844 Total 235,370 Source: Result of GIS Matrix Analysis of Landsat 5 TM 1990 and Landsat 7 ETM 2014 using ERDAS 9. 1 and LCM Idrisi TerrSet v. and Data Analysis Research . In the period of 1990-2014, there were many changes of land cover areas into settlements in LEA such as forest areas which became settlements for 98,254. 3 ha. It means that the loss of carbon stocks in forest area was 173,348,096,404 ton. The cultivation area becoming settlements was for 132,380. ha, which indicated 19,401,627,456 ton of carbon stock loss. The land cover changes also occurred in paddy field area in which it became settlements for 876. 1 ha which means 79,952,886 ton carbon stock loss. Then, the changes of plantation areas becoming residential areas were for 3,445. 2 ha, and it indicated the loss of carbon stocks for 1,140,257. 844 ton. Figure 4. Carbon Loss in The Leuser Ecosystem Area (LEA) It was found that the biggest carbon stock loss in LEA happened because of the land cover changes of forest areas into settlements for 173,348,096. 404 ton from 1990 to 2014. Hermon . explains that the loss of carbon stocks was triggered by land cover changes into settlements which kept increasing through conversion of forest, shrub, and paddy field into settlements. Hermon . elaborates that these land cover changes into settlements cause the removal of carbon stocks in the forest into the atmosphere which then become CO2 through deforestation and land burning. This condition will cause the accumulation of CO2 in the atmosphere. Forum Geografi. Vol 29 . December 2015: 187-196 Estimate of Changes. (Hermo. Conclusion Land cover changes occurred because of people activities which are related to economy and settlements. The changes of land cover will directly change the amount of carbon stock in an area. From 1990-2014, there was a big change of land cover happened in LEA. Land cover of paddy field and settlements were increasing a lot in 2014. land cover of forest, cultivation, shrub, and plantation was decreasing in 2014. In addition, the changes of land cover becoming settlement were the changes dominantly happened in LEA compared to other land cover. This condition caused the decrease of carbon stocks in LEA in 2014 compared to carbon stocks in 1990 for each land cover. The big changes of either land cover of forest or other land covers into settlements had cause the loss of carbon stocks in LEA for 194,049,235. 370 ton from 1990 to References