Open Access
18 March 2020 Rapid generation of global forest cover map using Landsat based on the forest ecological zones
Xiaomei Zhang, Tengfei Long, Guojin He, Yantao Guo, Ranyu Yin, Zhaoming Zhang, Han Xiao, Moxuan Li, Bo Cheng
Author Affiliations +
Abstract

The easy and ready access to Landsat datasets and the ever-lowering costs of computing make it feasible to monitor the Earth’s land cover at Landsat resolutions of 30 m. However, producing forest-cover products rapidly and on a large scale, such as intercontinental or global, is still a challenging task. By utilizing the huge catalog of satellite imagery as well as the high-performance computing capacity of Google Earth Engine, we proposed an automated pipeline for generating 30-m resolution global-scale forest map from time-series of Landsat images. We describe the methods to create products of forest cover at a global scale. First, we partitioned the landscapes into subregions of similar forest type and spatial continuity. Then, a multisource forest/nonforest sample set was established for machine algorithm learning training. Finally, a random forest classifier algorithm was used to obtain samples automatically, extract the characteristics of satellite images, and establish the forest/nonforest classifier models. Taking Landsat8 images in 2018 as a case, a novel 30-m resolution global forest cover (GFC30) map has been produced. The result shows that by the end of 2018, the total forest area in the world was 3.71  ×  109  ha. The accuracy evaluation of GFC30 for 2018 was carried out using verification points via stratified random sampling of a MODIS land cover map (MCD12C1 product in 2012) and verified on high-resolution satellite imagery (e.g., Google Earth). According to the validation result, the overall accuracy of GFC30 for 2018 is 90.94%.

1.

Introduction

Forests cover about 30.6% of the Earth’s land area and constitute a critical terrestrial ecosystem. Forest cover change (FCC) is highly relevant to the global carbon cycle, water supplies, biodiversity richness, and for understanding the rates and causes of land use change. As global ecological environment changes and population growth and ensuing human activities intensify, global forest cover (GFC) has decreased from 4128×106  ha in 1990 to 3999×106  ha in 2015. There was a net loss of some 129×106  ha of forest between 1990 and 2015, which was about the size of South Africa, representing an annual net loss rate of 0.13%.1 Yet deforestation, or forest conversion to other land use, is more complicated than that. Therefore, forest cover mapping has important practical significance and scientific value in terms of the spatial and temporal detailed change on global-scale forest.2

In recent years, there has been an increasing need for 30-m forest cover mapping because of the finer scale of forest change especially those resulting from anthropogenic factors.35 Mapping forest cover and FCC are two of the most common uses of Landsat data. However, Landsat data have been used at relatively local or national scales for land cover mapping. Peter Potapov et al.,4 Song et al.,5 and Huang et al.6 are some of the few researchers who studied wall-to-wall change detection at national scales. The Forest Resource Assessment (FRA) of the United Nations’ Food and Agriculture Organization (FAO) carried out the first systematic estimates of global forest land use and change between 1990 and 2005.7 More recently, Landsat samples, along with wall-to-wall datasets, have been used to monitor forest loss in the tropics and subsequently for the globe with forest loss and gain since 21st century.810 Nevertheless, these approaches do not meet the need for continental- or global-scale forest cover mapping using Landsat data because of the long period of data processing and it often takes a few years to update. The other major constraint is the very large computational and storage demands in processing huge volumes of high-quality data. However, owing to Google Earth Engine (GEE), a new generation of cloud computing platforms with access to a huge catalog of satellite imagery and global-scale analysis capabilities is now available. It is now possible to perform global-scale geospatial analysis efficiently without caring about preprocessing of satellite images.11

GEE is a cloud-based platform that makes it easy to access high-performance computing resources for processing very large geospatial datasets, without suffering the pains surrounded. Midekisa et al.12 used Landsat on GEE for land cover change over continental Africa and found it overcome the computational challenges of handling big earth data. Sidhu et al.13 used GEE to detect land cover change in Singapore. Although those works tried to use GEE to serve regional or continual land cover mapping, results of global scale have not been reported. However, with access to a huge catalog of satellite imagery and global-scale analysis capabilities, it is possible to perform parallel analysis and operation efficiently on GEE for rapid production of global mapping.

Since mapping over large landscapes typically involves many satellite scenes and a complicated classifier, it will cost a significant amount of time to process the globe as a file. A common method is to stratify landscapes into subregions of similar biophysical and spectral characteristics. This process is not new to remote sensing and has been widely used as a method to improve accuracy and efficiency.1417 In 1990, FAO has developed an ecological zone covering only the tropical areas to presents forest data, and now a Global Ecological Zone (GEZ) was developed over years, which can be downloaded at Ref. 18. The new GEZ map has some ecological meaning that can be more generally understood as broad forest types (e.g., tropical rain forests and boreal forests). Therefore, we can use the ecological zones as areas with similar features and grouped into a single file.

In addition, a large number of high-quality sample points are very important for global products. So far, many of the land cover sample sets and related services have been publicly released worldwide [such as 30-m or coarse resolution global land cover (GLC) maps, Crowdsourced data]. Making full use of the existing data is an effective way to solve the problem of large-scale global sample points.

In this study, we test an automated approach for forest cover mapping with Landsat images in GEE. By utilizing the forest ecological zones (FEZs) as a processing unit, making full use of the existing data to obtain global forest sample points, as well as with the huge catalog of satellite imagery on GEE, we proposed an automated pipeline method for generating 30-m resolution global-scale forest cover map. A novel 30-m resolution global forest map of 2018 has been produced and was verified by accuracy assessment.

2.

Methodology

2.1.

Forest Ecological Zone Map

Since global mapping usually involves a great amount of data and a complicated classifier, areas with similar features are grouped into a single file; the FEZ map classification is one of them.18 The underlying concept of FEZ delineation is a preclassification division of the landscape into a finite number of units that represent relative homogeneity with respect to landform, soil, vegetation, spectral reflectance, and image footprints at a project scale that is affordable.

The FEZs are based on several existing global maps, starting with the FAO GEZ map, a map designed for reporting forest and forest change statistics in the context of the FRAs.19,20 The GEZ map is basically a map of natural vegetation types. Based on GEZ map, the type of main forest is extracted, and the other vegetation types are merged, and at the same time the boundary is modified by reference to several global products primarily developed for land cover or forest cover. Forest and nonforest areas were included in order to provide global coverage, and there are 45 FEZs in global region. The 45 FEZs are identified by a code from 1 to 45 (Fig. 1). Classification using FEZs can not only optimize the classifiers, but because the ecological zones are independent, they can also be processed in parallel to reduce processing time.

Fig. 1

FEZ map, spatial extent of 45 FEZs representing different landscapes for global forest mapping, identified by codes from 01 to 45.

JARS_14_2_022211_f001.png

2.2.

Multisource Reference Data Integration

A large number of high-quality sample points are an important guarantee for extrapolating forest classification from national to global scale. At the global scale, there are a variety of reference datasets that can be used to support 30-m GLC mapping, such as existing GLC maps at coarser resolution, 30 m or higher resolution of regional land cover data. Online-distributed geospatial datasets and services (such as GEE, Map World, and Open Street Map), as well as land cover-related services (such as Geo-Wiki and Global Crowdsourced data) also provide valuable external and interoperable ancillary sources of information for forests.2123

Ancillary data are less uniform than satellite image data, varying in format, accuracy, and spatial resolution. To facilitate the use of such data and their incorporation into classification and validation processes, all the ancillary data were processed and checked carefully. When all the reference data were combined, they were divided into each FEZ and checked by experts for the balance of all forest and nonforest categories. The samples were supplemented by interpretation from high-resolution images, such as Google map. Under the premise of ensuring no less than 1000 sample points per ecological zones, a total of 61,653 points were collected for training datasets and the distribution of the points is shown in Fig. 2.

Fig. 2

Spatial distribution of sample points used for training datasets, which was grouped into 45 FEZs, can be used for every FEZ separately.

JARS_14_2_022211_f002.png

2.3.

Forest Cover Mapping via Google Earth Engine

In this study, the definition of forest is the same as used in FRA of FAO, that is, land spanning more than 0.5 ha with trees higher than 5 m and a canopy cover of more than 10%, or trees able to reach these thresholds in situ.24

A FEZ-based classification approach was developed, as shown in Fig. 3, which mainly consists of three steps, data preprocessing, feature selection, and accuracy assessment. This method takes the FEZs as the processing unit and processes the classification of each zone in parallel in GEE and generates GFC products as results. GEE can combine FEZs and other classification techniques well.

Fig. 3

Overall flowchart of forest cover mapping using GEE.

JARS_14_2_022211_f003.png

2.3.1.

Data preprocessing

In this study, Landsat 8 (OLI) surface reflectance data, which were computed using the Landsat Ecosystem Disturbance Adaptive Processing System, were used.25,26 A cloud screening algorithm was applied using quality assessment (QA) bands in order to remove snow- and cloud-contaminated pixels for each Landsat image.27 Annual composites were then produced by taking the median value from images in the target year, plus or minus one year.

In addition to satellite image data, digital elevation model (DEM) and global reference sample points grouped on FEZs were another input data sources. The global training data consisted of 23,569 forest and 38,084 nonforest samples, which were collected from multisource and generated by stratified random sampling (mentioned in Sec. 2.2). DEM is used to derive terrain information.

2.3.2.

Feature selection and classification

In addition to producing raw image spectral characters, textural information, as well as terrain features were computed and combined as the input features.

To better finish the analysis on green vegetation’s abundance and activity, a series of spectral vegetation indices, based on the diverse spectral features of forest, were set up in past decades. Normalized difference vegetation index (NDVI) and enhanced vegetation index (EVI), as examples of those indices, have different utilities on the vegetation with different height. NDVI exaggerates the saturation using nonlinear model, which improves the monitoring on low-mid vegetation but does not apply well to high-vegetation cover. On the other hand, EVI, which is generated using the surface reflectance bands 2 (blue), 4 (red), and 5 (near-infrared) of Landsat8, have better performance on high-vegetation cover, because the interference from canopy backgrounds is reduced with this algorithm. Recent research and analysis have shown evidence that vegetation index is effective in distinguishing vegetation area with specific geographical features using spectral characteristics.2830

Unfortunately, spectral characteristics would be interfered when it is applied on a global scale due to the variation of forest types and conditions. Therefore, the textures, which are a kind of characteristic that reflects the roughness of object surface, are sometimes necessarily used to further extract forest information, because some other geographical features such as shrub or plants have similar spectral characters. In this case, the gray-level co-occurrence matrix is introduced to extract the texture characteristics that we need for forest distinction. According to the research by Zhang et al.,3134 the mean of the eight features, which were calculated from the multispectral bands (bands 1 to 7) of the Landsat 8 is the most prominent, and the optimal window size is 19. Furthermore, the vertical zoning and slope or aspect play important roles on the vegetation distribution in certain high-altitude regions such as southwest Tibet. Therefore, this study selected DEM and its derivative data as input features at those regions.

The random forest (RF) algorithm provided by GEE was applied to train a decision classifier. RF classifier with a higher number of decision trees usually provides better results but causes higher cost in computation time. Since the input features of the algorithm that have high sensitivity to forest cover were well selected, as shown in Ref. 31, we limited the number of decision trees in the forest to 100 for trade-off between accuracy and efficiency.

2.3.3.

Accuracy assessment

In terms of guaranteeing the accuracy of GFC map and the completeness of QA, a stratified random sampling method was used to generate points for the validation. At the same time, in order to make these generated points to represent the major biomes identified by Olson et al.,19 we use the MODIS land cover map [MCD12C1 product in 2012, using University of Maryland (UMD) scheme] to partition the Earth’s land surface into 14 land cover classes. The forest classes were then merged into five categories based on their similarities, including evergreen broad-leaf forest, evergreen needle-leaf forest, deciduous broad-leaf forest, deciduous needle-leaf forest, and mixed forest, and the nonforest classes included four categories, such as shrub, meadow, farmland, and water body. A total of 1500 points are randomly selected for each class and the reliability of those validation points are guaranteed by careful checking.

3.

Results and Analysis

3.1.

Forest Cover Map

With the methodology and reference data described in Sec. 2.3, based on the database and RF classifier algorithm provided on GEE, a 30-m-resolution GFC for 2018 (GFC30,2018), as shown in Fig. 4, is generated, which was projected in a geographical (Lat/Long) projection at 0.00025 deg (  30  m) resolution, with the WGS84 horizontal datum and the EGM96 vertical datum. The result consisted of 10×10  (deg) tiles ranges from 180 W to 180 E and 80 N to 60 S, which can be freely downloaded from Ref. 35.

Fig. 4

Global forest and climate zone map.

JARS_14_2_022211_f004.png

According to statistical results, the total area of global forest in 2018 is about 3815×106  ha, which makes up   25.60% of the whole land area (about 15×109  ha). The global forest distribution is shown in Fig. 4. The global forests are unequally distributed, with zonal distribution along latitudes. These major forests include South America, the tropical rainforest area in Southeast Asia and Central Africa, the boreal forest area in Russia and Canada, and the Pacific coast and Atlantic coast. This distribution has certain relevance with the pattern of global climate zones.

The world is divided into four climatic zones, which are tropical, subtropical, temperate, and northern frigid. The distribution of global forest is spatially uneven in different climatic zones. From large to small, the forest area is tropical, northern frigid, temperate, and subtropical, as shown in Table 1 and Fig. 5. Tropic has the greatest forest area of 1.847×109  ha, accounting for 48.40% of the global forest area, which is almost a half of the GFC. While subtropical zone has the smallest forest area of 383×106  ha, accounting for 10.12%.

Table 1

Forest distribution of each climate zone and proportion of GFC.

Climate zoneForest cover (1000  hm2)Proportion of global forest area (%)
Northern frigid zone964,940.7125.51
Subtropical zone382,825.4610.12
Temperate zone587,453.4415.53
Tropical zone1,846,715.7048.83

Fig. 5

Forest distribution of each climate zone and proportion of global forest area.

JARS_14_2_022211_f005.png

The regional distribution of global forest has significant relation with temperature and precipitation. Generally, high temperature makes the growth period of vegetation longer, and abundant precipitation can improve the status of vegetation growth.

In the aspects of continental views, the forest distribution in six continents also has big differences (Fig. 6). Table 2 shows the figure of forest cover of each continent and proportion of global forest. From the table, it can be seen that the forest cover in Asia is the largest on Earth, mainly because of the broad north forest in Russia. Owing to its relatively small area, Oceania is the continent with the least forest. And South America has the highest forest coverage rate, mainly because of the Amazon rainforest, the world’s largest and contiguous tropical rainforest.

Fig. 6

Statistic map of GFC in continents.

JARS_14_2_022211_f006.png

Table 2

Forest cover of each continent and proportion of global forest.

ContinentsForest cover (1000  hm2)Forest coverage rate (%)
Africa513,904.6017.00
Asia1,179,399.9826.46
Europe367,117.7636.06
North America767,298.3631.05
Oceania137,195.3316.07
South America850,273.8247.66

3.2.

Validation Result

Around the world, 39,900 points created in Sec. 2.3.3 are selected as points for final validation. The distribution of these validation points for GFC Product 2018 is shown in Fig. 7. According to the validation result, the overall accuracy (OA) of GFC30 (2018) is 90.94%.

Fig. 7

Distribution of global validation points.

JARS_14_2_022211_f007.png

To better analyze the accuracy of our product, the accuracy of GFC30 across the six continents was also validated (Table 3). Accuracy for Oceania, Europe, and South America was relatively high, namely, 95.59%, 94.25%, and 91.79%, respectively. The main reason is that the remote sensing images for these areas have high cover rate so that there is a large amount of available and high-quality data for these areas. As an example, South America has dense tropical rainforest, high forest cover rate, and less influence from seasonal change. Therefore, with little limitation on temporal phases, the data for these regions have high quality.

Table 3

Preliminary accuracy assessment of forest cover 2018.

ContinentsProduct’s accuracy (%)User’s accuracy (%)OA (%)
Africa90.4385.4388.40
Asia92.6589.0591.29
Europe94.9595.6694.25
North America92.1978.8685.82
Oceania93.9589.0095.59
South America96.3389.5191.79
Global93.9587.1290.94

However, the accuracy of the data for Africa is not as good as expected. One important reason is that the trees in Savanna, which is the transverse zone of forest and grassland at the north and south of Africa, are distributed unevenly. Thus, the cover rate is difficult to be identified. In addition, Savanna regions have distinct climates for wet and dry seasons, and hence the cover of deciduous forests changes significantly with seasons. Therefore, the selected images may not contain the most accurate data, leading to the difference in the result of analysis and lower accuracy.

4.

Conclusions

Forests are essential for human well-being, sustainable development, and the health of the Earth system. The rapid development of 30-m-resolution forest cover products worldwide can provide an important source of information and a reference for people to study the status and changes of forests.

In this study, we propose an automated pipeline for generating 30-m-resolution global-scale forest cover map utilizing GEE. Different from the previous GFC product, the proposed FEZ-based approach uses FEZs to divide the global forest into 45 zones, accelerate the global product production speed and efficiency by introducing the GEE platform, and uses the RF algorithm for parallel. The method and result can provide experience for big data analysis and technical supports for analysis and creating products of land covers.

Based on the proposed method, a novel 30-m-resolution GFC map of year 2018, with the OA of 90.94%, was produced. GFC30 provides reliable and valid data support for the analysis of forest cover states in different scales, including the spatial distribution of global forest, forest cover states for each continent, and the forest cover states of highly concerned areas, such as the Amazon River Basin, the Congo River Basin, and Southeast Asia. In addition, various statistics and conclusions provided by the GFC 2018 can provide the relevant departments with information support and decision-making services.

However, GFC2018 product has weaknesses. In Africa, due to the influence of the distribution of cloud and rain, and the lack of availability of high-quality optical images, the product shows lesser accuracy. The radar data, which are available freely via Sentinel satellites, could be utilized to improve the product’s quality. On the other hand, this study has used lots of samples for classification, and the future research should focus on how to realize the high-quality production with lower or smaller samples of points.

For farther research, based on GFC 2018, our research group will continue to work for the development of FCC products, diversifying the forest cover products and analyzing the change trend of forest, forest disturbance, and its influence on the ecosystem.

Acknowledgments

This research has been supported by the National Key Research and Development Program of China (2016YFA0600302), the National Natural Science Foundation of China (61731022), and the 2019 Global Ecosystems and Environment Observation Analysis Research Cooperation “Global forest cover and changes.”

References

1. 

Global Forest Resources Assessment 2015. How Are the World’s Forests Changing?, 2nd ed.Food and Agriculture Organization of the United Nations, Rome (2016). Google Scholar

2. 

J. R. Townshend et al., “Global characterization and monitoring of forest cover using Landsat data: opportunities and challenges,” Int. J. Digital Earth, 5 (5), 373 –397 (2012). https://doi.org/10.1080/17538947.2012.713190 Google Scholar

3. 

J. R. Townshend et al., Remote Sensing and Digital Image Processing, Land Remote Sensing and Global Environmental Change, Springer, New York (2010). Google Scholar

4. 

P. Potapov et al., “Regional-scale boreal forest cover and change mapping using Landsat data composites for European Russia,” Remote Sens. Environ., 115 548 –561 (2011). https://doi.org/10.1016/j.rse.2010.10.001 Google Scholar

5. 

D.-X. Song et al., “Use of Landsat and Corona data for mapping forest cover change from the mid-1960s to 2000s: case studies from the Eastern United States and Central Brazil,” ISPRS J. Photogramm. Remote Sens., 103 81 –92 (2015). https://doi.org/10.1016/j.isprsjprs.2014.09.005 IRSEE9 0924-2716 Google Scholar

6. 

C. Huang et al., “Rapid loss of Paraguay’s Atlantic forest and the status of protected areas—a Landsat assessment,” Remote Sens. Environ., 106 460 –466 (2007). https://doi.org/10.1016/j.rse.2006.09.016 Google Scholar

7. 

Global Forest Land-Use Change 1990–2005, Food and Agriculture Organization of the United Nations and European Commission Joint Research Centre. FAO, Rome (2012). Google Scholar

8. 

M. Hansen et al., “Humid tropical forest clearing from 2000 to 2005 quantified using multi-temporal and multi-resolution remotely sensed data,” Proc. Natl. Acad. Sci. U. S. A, 105 (27), 9439 –9444 (2008). https://doi.org/10.1073/pnas.0804042105 Google Scholar

9. 

M. C. Hansen et al., “Quantification of global gross forest cover loss,” Proc. Natl. Acad. Sci. U. S. A., 107 8650 –8655 (2010). https://doi.org/10.1073/pnas.0912668107 Google Scholar

10. 

M. C. Hansen et al., “High-resolution global maps of 21st-century forest cover change,” Science, 342 850 –853 (2013). https://doi.org/10.1126/science.1244693 SCIEAS 0036-8075 Google Scholar

11. 

N. Gorelick et al., “Google Earth Engine: planetary-scale geospatial analysis for everyone,” Remote Sens. Environ., 202 18 –27 (2017). https://doi.org/10.1016/j.rse.2017.06.031 Google Scholar

12. 

A. Midekisa et al., “Mapping land cover change over continental Africa using Landsat and Google Earth Engine cloud computing,” PLoS One, 12 (9), e0184926 (2017). https://doi.org/10.1371/journal.pone.0184926 POLNCL 1932-6203 Google Scholar

13. 

N. Sidhu et al., “Using Google Earth Engine to detect land cover change: Singapore as a use case,” Eur. J. Remote Sens., 51 (1), 486 –500 (2018). https://doi.org/10.1080/22797254.2018.1451782 Google Scholar

14. 

J. D. White et al., “Forest mapping at Lassen Volcanic National Park, California, using Landsat TM data and a geographical information system,” Photogramm. Eng. Remote Sens., 61 299 –305 (1995). Google Scholar

15. 

L. R. Pettinger, “Digital classification of Landsat data for vegetation and land-cover mapping in the Blackfoot River Watershed, Southeastern Idaho,” U. S. Geol. Surv. Prof. Pap. (1982). Google Scholar

16. 

T. M. Lillisand, “A protocol for satellite-based land cover classification in the upper Midwest. Gap analysis: a landscape approach to biodiversity planning,” ASPRS, 320 (1996). Google Scholar

17. 

C. G. Homer et al., “Land cover-type modeling using multi-scene Thematic Mapper mosaic,” Photgramm. Eng. Remote Sens., 63 59 –67 (1997). Google Scholar

18. 

Global Ecological Zones for FAO Forest Reporting: 2010 Update. Forest Resources Assessment Working Paper N. 179, 42 FAO, Rome (2012). http://foris.fao.org/static/data/fra2010/ecozones2010.jpg Google Scholar

19. 

D. M. Olson et al., “Terrestrial ecoregions of the world: a new map of life on Earth,” BioScience, 51 (11), 933 –938 (2001). https://doi.org/10.1641/0006-3568(2001)051[0933:TEOTWA]2.0.CO;2 BISNAS 0006-3568 Google Scholar

20. 

D. M. Olson and E. Dinerstein, “The Global 200: priority ecoregions for global conservation,” Ann. Mo. Bot. Gard, 89 (2), 199 –224 (2002). https://doi.org/10.2307/3298564 Google Scholar

21. 

S. Fritz et al., “Geo-Wiki: an online platform for improving global land cover,” Environ. Modell. Software, 31 110 –123 (2012). https://doi.org/10.1016/j.envsoft.2011.11.015 Google Scholar

22. 

L. Yu and P. Gong, “Google Earth as a virtual globe tool for earth science applications at the global scale: progress and perspectives,” Int. J. Remote Sens., 33 (12), 3966 –3986 (2012). https://doi.org/10.1080/01431161.2011.636081 IJSEDK 0143-1161 Google Scholar

23. 

S. Fritz et al., “Data descriptor: a global dataset of crowdsourced land cover and land use reference data,” Sci. Data, 4 170075 (2017). https://doi.org/10.1038/sdata.2017.75 Google Scholar

24. 

FRA 2015 Terms and Definitions, Food and Agriculture Organization of the United Nations, Rome (2012). Google Scholar

25. 

J. G. Masek et al., “A Landsat surface reflectance dataset for North America, 1990-2000,” IEEE Geosci. Remote Sens. Lett., 3 (1), 68 –72 (2006). https://doi.org/10.1109/LGRS.2005.857030 Google Scholar

26. 

E. Vermote et al., “Preliminary analysis of the performance of the Landsat 8/OLI land surface reflectance product,” Remote Sens. Environ., 185 46 –56 (2016). https://doi.org/10.1016/j.rse.2016.04.008 Google Scholar

27. 

Z. Zhu and C. E. Woodcock, “Automated cloud, cloud shadow, and snow detection in multitemporal Landsat data: An algorithm designed specifically for monitoring land cover change,” Remote Sens. Environ., 152 217 –234 (2014). https://doi.org/10.1016/j.rse.2014.06.012 Google Scholar

28. 

D. Haboudane et al., “Hyperspectral vegetation indices and novel algorithms for predicting green LAI of crop canopies: modeling and validation in the context of precision agriculture,” Remote Sens. Environ., 90 337 –352 (2004). https://doi.org/10.1016/j.rse.2003.12.013 Google Scholar

29. 

L. Vescovo and D. Gianelle, “Using the MIR bands in vegetation indices for the estimation of grassland biophysical parameters from satellite remote sensing in the Alps region of Trentino (Italy),” Adv. Space Res., 41 1764 –1772 (2008). https://doi.org/10.1016/j.asr.2007.07.043 ASRSDW 0273-1177 Google Scholar

30. 

Z. Jiang et al., “Analysis of NDVI and scaled difference vegetation index retrievals of vegetation fraction,” Remote Sens. Environ., 101 (3), 366 –378 (2006). https://doi.org/10.1016/j.rse.2006.01.003 Google Scholar

31. 

X. M. Zhang, “Research on land cover classification based on random forest classifier,” Institute of Remote Sensing and Digital Earth, University of Chinese Academy of Sciences(2017). Google Scholar

32. 

J. Beekhuizen and K. C. Clarke, “Toward accountable land use mapping: using geocomputation to improve classification accuracy and reveal uncertainty,” Int. J. Appl. Earth Obs. Geoinf., 12 127 –137 (2010). https://doi.org/10.1016/j.jag.2010.01.005 Google Scholar

33. 

F. Pacifici, M. Chini and W. J. Emery, “A neural network approach using multiscale textural metrics from very high-resolution panchromatic imagery for urban land-use classification,” Remote Sens. Environ., 113 1276 –1292 (2009). https://doi.org/10.1016/j.rse.2009.02.014 Google Scholar

34. 

X. M. Zhang et al., “Spectral-spatial multi-feature classification of remote sensing big data based on a random forest classifier for land cover mapping,” Cluster Comput., 20 (3), 2311 –2321 (2017). https://doi.org/10.1007/s10586-017-0950-0 Google Scholar

Biography

Xiaomei Zhang is a senior engineer at the Aerospace Information Research Institute. She received her BS degree from Jilin University in 2001, and her MS degree and PhD in cartography and geographical information system from the University of Chinese Academy of Sciences, Beijing, China. Her current research interests include intelligent information processing and application of remote sensing.

Biographies of the other authors are not available.

CC BY: © The Authors. Published by SPIE under a Creative Commons Attribution 4.0 Unported License. Distribution or reproduction of this work in whole or in part requires full attribution of the original publication, including its DOI.
Xiaomei Zhang, Tengfei Long, Guojin He, Yantao Guo, Ranyu Yin, Zhaoming Zhang, Han Xiao, Moxuan Li, and Bo Cheng "Rapid generation of global forest cover map using Landsat based on the forest ecological zones," Journal of Applied Remote Sensing 14(2), 022211 (18 March 2020). https://doi.org/10.1117/1.JRS.14.022211
Received: 9 October 2019; Accepted: 27 February 2020; Published: 18 March 2020
Lens.org Logo
CITATIONS
Cited by 22 scholarly publications.
Advertisement
Advertisement
KEYWORDS
Earth observing sensors

Landsat

Satellites

Vegetation

Satellite imaging

Associative arrays

Climatology

RELATED CONTENT


Back to Top