A 30 m terrace mapping in China using Landsat 8 imagery and digital elevation model based on the Google Earth Engine

<p>The construction of terraces is a key soil conservation practice on agricultural land in China providing multiple valuable ecosystem services. Accurate spatial information on terraces is needed for both management and research. In this study, the first 30 m resolution terracing map of the e...

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Main Authors: B. Cao, L. Yu, V. Naipal, P. Ciais, W. Li, Y. Zhao, W. Wei, D. Chen, Z. Liu, P. Gong
Format: Article
Language:English
Published: Copernicus Publications 2021-06-01
Series:Earth System Science Data
Online Access:https://essd.copernicus.org/articles/13/2437/2021/essd-13-2437-2021.pdf
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author B. Cao
L. Yu
L. Yu
V. Naipal
P. Ciais
W. Li
W. Li
Y. Zhao
Y. Zhao
W. Wei
D. Chen
Z. Liu
P. Gong
P. Gong
author_facet B. Cao
L. Yu
L. Yu
V. Naipal
P. Ciais
W. Li
W. Li
Y. Zhao
Y. Zhao
W. Wei
D. Chen
Z. Liu
P. Gong
P. Gong
author_sort B. Cao
collection DOAJ
description <p>The construction of terraces is a key soil conservation practice on agricultural land in China providing multiple valuable ecosystem services. Accurate spatial information on terraces is needed for both management and research. In this study, the first 30 m resolution terracing map of the entire territory of China is produced by a supervised pixel-based classification using multisource and multi-temporal data based on the Google Earth Engine (GEE) platform. We extracted time-series spectral features and topographic features from Landsat 8 images and the Shuttle Radar Topography Mission digital elevation model (SRTM DEM) data, classifying cropland area (cultivated land of Globeland30) into terraced and non-terraced types through a random forest classifier. The overall accuracy and kappa coefficient were evaluated by 10 875 test samples and achieved values of 94 % and 0.72, respectively. For terrace class, the producer's accuracy (PA) was 79.945 %, and the user's accuracy (UA) was 71.149 %. The classification performed best in the Loess Plateau and southwestern China, where terraces are most numerous. Some northeastern, eastern-central, and southern areas had relatively high uncertainty. Typical errors in the mapping results are from the sloping cropland (non-terrace cropland with a slope of <span class="inline-formula">≥</span> 5<span class="inline-formula"><sup>∘</sup></span>), low-slope terraces, and non-crop vegetation. Terraces are widely distributed in China, and the total terraced area was estimated to be 53.55 Mha (i.e., 26.43 % of China's cropland area) by pixel counting (PC) method and 58.46 <span class="inline-formula">±</span> 2.99 Mha (i.e., 28.85 % <span class="inline-formula">±</span> 1.48 % of China's cropland area) by error-matrix-based model-assisted estimation (EM) method. Elevation and slope were identified as the main features in the terrace/non-terrace classification, and multi-temporal spectral features (such as percentiles of NDVI, TIRS2, and BSI) were also essential. Terraces are more challenging to identify than other land use types because of the intra-class feature heterogeneity, interclass feature similarity, and fragmented patches, which should be the focus of future research. Our terrace mapping algorithm can be used to map large-scale terraces in other regions globally, and our terrace map will serve as a landmark for studies on multiple ecosystem service assessments including erosion control, carbon sequestration, and biodiversity conservation. The China terrace map is available to the public at <a href="https://doi.org/10.5281/zenodo.3895585">https://doi.org/10.5281/zenodo.3895585</a> (Cao et al., 2020).</p>
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spelling doaj.art-f0ba3422296b414096e006fba4909e032022-12-21T18:50:28ZengCopernicus PublicationsEarth System Science Data1866-35081866-35162021-06-01132437245610.5194/essd-13-2437-2021A 30&thinsp;m terrace mapping in China using Landsat 8 imagery and digital elevation model based on the Google Earth EngineB. Cao0L. Yu1L. Yu2V. Naipal3P. Ciais4W. Li5W. Li6Y. Zhao7Y. Zhao8W. Wei9D. Chen10Z. Liu11P. Gong12P. Gong13Ministry of Education Key Laboratory for Earth System Modeling, Department of Earth System Science, Tsinghua University, Beijing 100084, ChinaMinistry of Education Key Laboratory for Earth System Modeling, Department of Earth System Science, Tsinghua University, Beijing 100084, ChinaMinistry of Education Ecological Field Station for East Asian Migratory Birds, Beijing 100084, ChinaDepartment of Geography, Faculty of Geosciences, Ludwig-Maximilian University, Munich, GermanyLaboratoire des Sciences du Climat et de l'Environnement, CEA-CNRS-UVSQ, UMR8212, Gif-sur-Yvette, FranceMinistry of Education Key Laboratory for Earth System Modeling, Department of Earth System Science, Tsinghua University, Beijing 100084, ChinaMinistry of Education Ecological Field Station for East Asian Migratory Birds, Beijing 100084, ChinaCollege of Land Science and Technology, China Agricultural University, Beijing 100083, ChinaKey Laboratory of Remote Sensing for Agri-Hazards, Ministry of Agriculture and Rural Affairs, Beijing 100083, ChinaState Key Laboratory of Urban and Regional Ecology, Research Center for Eco-environmental Sciences, Chinese Academy of Sciences, Beijing 100085, ChinaState Key Laboratory of Urban and Regional Ecology, Research Center for Eco-environmental Sciences, Chinese Academy of Sciences, Beijing 100085, ChinaMinistry of Education Key Laboratory for Earth System Modeling, Department of Earth System Science, Tsinghua University, Beijing 100084, ChinaMinistry of Education Key Laboratory for Earth System Modeling, Department of Earth System Science, Tsinghua University, Beijing 100084, ChinaMinistry of Education Ecological Field Station for East Asian Migratory Birds, Beijing 100084, China<p>The construction of terraces is a key soil conservation practice on agricultural land in China providing multiple valuable ecosystem services. Accurate spatial information on terraces is needed for both management and research. In this study, the first 30 m resolution terracing map of the entire territory of China is produced by a supervised pixel-based classification using multisource and multi-temporal data based on the Google Earth Engine (GEE) platform. We extracted time-series spectral features and topographic features from Landsat 8 images and the Shuttle Radar Topography Mission digital elevation model (SRTM DEM) data, classifying cropland area (cultivated land of Globeland30) into terraced and non-terraced types through a random forest classifier. The overall accuracy and kappa coefficient were evaluated by 10 875 test samples and achieved values of 94 % and 0.72, respectively. For terrace class, the producer's accuracy (PA) was 79.945 %, and the user's accuracy (UA) was 71.149 %. The classification performed best in the Loess Plateau and southwestern China, where terraces are most numerous. Some northeastern, eastern-central, and southern areas had relatively high uncertainty. Typical errors in the mapping results are from the sloping cropland (non-terrace cropland with a slope of <span class="inline-formula">≥</span> 5<span class="inline-formula"><sup>∘</sup></span>), low-slope terraces, and non-crop vegetation. Terraces are widely distributed in China, and the total terraced area was estimated to be 53.55 Mha (i.e., 26.43 % of China's cropland area) by pixel counting (PC) method and 58.46 <span class="inline-formula">±</span> 2.99 Mha (i.e., 28.85 % <span class="inline-formula">±</span> 1.48 % of China's cropland area) by error-matrix-based model-assisted estimation (EM) method. Elevation and slope were identified as the main features in the terrace/non-terrace classification, and multi-temporal spectral features (such as percentiles of NDVI, TIRS2, and BSI) were also essential. Terraces are more challenging to identify than other land use types because of the intra-class feature heterogeneity, interclass feature similarity, and fragmented patches, which should be the focus of future research. Our terrace mapping algorithm can be used to map large-scale terraces in other regions globally, and our terrace map will serve as a landmark for studies on multiple ecosystem service assessments including erosion control, carbon sequestration, and biodiversity conservation. The China terrace map is available to the public at <a href="https://doi.org/10.5281/zenodo.3895585">https://doi.org/10.5281/zenodo.3895585</a> (Cao et al., 2020).</p>https://essd.copernicus.org/articles/13/2437/2021/essd-13-2437-2021.pdf
spellingShingle B. Cao
L. Yu
L. Yu
V. Naipal
P. Ciais
W. Li
W. Li
Y. Zhao
Y. Zhao
W. Wei
D. Chen
Z. Liu
P. Gong
P. Gong
A 30&thinsp;m terrace mapping in China using Landsat 8 imagery and digital elevation model based on the Google Earth Engine
Earth System Science Data
title A 30&thinsp;m terrace mapping in China using Landsat 8 imagery and digital elevation model based on the Google Earth Engine
title_full A 30&thinsp;m terrace mapping in China using Landsat 8 imagery and digital elevation model based on the Google Earth Engine
title_fullStr A 30&thinsp;m terrace mapping in China using Landsat 8 imagery and digital elevation model based on the Google Earth Engine
title_full_unstemmed A 30&thinsp;m terrace mapping in China using Landsat 8 imagery and digital elevation model based on the Google Earth Engine
title_short A 30&thinsp;m terrace mapping in China using Landsat 8 imagery and digital elevation model based on the Google Earth Engine
title_sort 30 thinsp m terrace mapping in china using landsat 8 imagery and digital elevation model based on the google earth engine
url https://essd.copernicus.org/articles/13/2437/2021/essd-13-2437-2021.pdf
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