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Annual oil palm plantation maps in Malaysia and Indonesia from 2001 to 2016

机译:2001年至2016年马来西亚和印度尼西亚的年度油棕榈种植园地图

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Increasing global demand of vegetable oils and biofuelsresults in significant oil palm expansion in southeastern Asia, predominatelyin Malaysia and Indonesia. The land conversion to oil palm plantations has posedrisks to deforestation (50 % of the oil palm was taken from forest during1990–2005; Koh and Wilcove, 2008), loss of biodiversity and greenhousegas emission over the past decades. Quantifying the consequences of oil palmexpansion requires fine-scale and frequently updated datasets of land coverdynamics. Previous studies focused on total changes for a multi-yearinterval without identifying the exact time of conversion, causinguncertainty in the timing of carbon emission estimates from land coverchange. Using Advanced Land Observing Satellite (ALOS) Phased Array typeL-band Synthetic Aperture Radar (PALSAR), ALOS-2 PALSAR-2 and ModerateResolution Imaging Spectroradiometer (MODIS) datasets, we produced an annualoil palm area dataset (AOPD) at 100 m resolution in Malaysia andIndonesia from 2001 to 2016. We first mapped the oil palm extent usingPALSAR and PALSAR-2data for 2007–2010 and 2015–2016 and then applied adisturbance and recovery algorithm (Breaks For Additive Season and Trend – BFAST) to detect land cover changetime points using MODIS data during the years without PALSAR data (2011–2014and 2001–2006). The new oil palm land cover maps are assessed to have anaccuracy of 86.61 % in the mapping step (2007–2010 and 2015–2016). Duringthe intervening years when MODIS data are used, 75.74 % of the detected changetime matched the timing of actual conversion using Google Earth andLandsat images. The AOPD revealed spatiotemporal oil palm dynamicsevery year and shows that plantations expanded from 2.59 to 6.39×10~(6) ha andfrom 3.00 to 12.66×10~(6) ha in Malaysia and Indonesia, respectively (i.e. a netincrease of 146.60 % and 322.46 %) between 2001 and 2016. The highertrends from our dataset are consistent with those from the nationalinventories, with limited annual average difference in Malaysia (0.2×10~(6) ha)and Indonesia (?0.17×10~(6) ha). We highlight the capability of combiningmultiple-resolution radar and optical satellite datasets in annualplantation mapping to a large extent by using image classification andstatistical boundary-based change detection to achieve long time series. Theconsistent characterization of oil palm dynamics can be further used indownstream applications. The annual oil palm plantation maps from 2001 to2016 at 100 m resolution are published in the Tagged Image File Format withgeoreferencing information (GeoTIFF) athttps://doi.org/10.5281/zenodo.3467071 (Xu et al., 2019).
机译:在东南亚,主要的马来西亚和印度尼西亚,增加了植物油和生物塑料的全球需求。油棕种植园的土地转换与森林砍伐(50%的油棕)在10090-2005期间取自森林; koh和Wilcove,2008年),过去几十年来的生物多样性和温室涌出的损失。量化油PalmExpansion的后果需要较微量的陆地覆盖动力学的微量和经常更新的数据集。以前的研究专注于多历史间隔的总变化,而无需识别转换的确切时间,在陆地覆盖的碳排放估计的时间中导致突触。采用先进的土地观测卫星(ALOS)相控阵列阵列曲线带合成孔径雷达(PALSAR),ALOS-2 PALSAR-2和体式化成像成像光谱仪(MODIS)数据集,我们在100米处生产了100米从2001年到2016年的马来西亚和印度尼西亚。我们首先使用Palsar和Palsar-2data映射了2007 - 2010和2015-2016,然后应用了Adissurbance和Recovery算法(添加剂季节和趋势 - BFast的休息)来检测陆地覆盖范围在没有PALSAR数据的多年期间使用MODIS数据(2011-2014和2001-2006)。评估新的油棕榈覆盖地图在绘图步骤中具有86.61%的ANAGURCURY(2007-2010和2015-2016)。在使用MODIS数据时,在使用MODIS数据期间,75.74%的检测到的Changetime使用Google地球和兰德斯坦图像匹配实际转换的时间。 AOPD揭示了马来西亚和印度尼西亚分别从2.59到6.39×10〜(6)公顷的2.59至6.39×10〜(6)HA的瞬间发芽的年度,并分别从2.59到12.66×10〜(6)公顷%)2001年至2016年之间。我们数据集的高度趋于与天国职业的趋势一致,马来西亚年平均差异有限(0.2×10〜(6)公顷)和印度尼西亚(?0.17×10〜(6)公顷) 。我们通过使用基于图像分类和统计基础的改变检测来突出显示有限的多分辨率雷达和光学卫星数据集的能力,以实现长时间序列。可以进一步使用油掌动态的表征油手掌动态的表征。 2001年至2016年的每年的油棕榈种植园地图以100米的分辨率发表于标记的图像文件格式(地理灯岛)AthTPS://Do.org/10.5281/zenodo.3467071(Xu等,2019)。

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