3.7. Analysis of the History and the Current Research Hotspots
In this study, there are 11,854 keywords detected in the 2692 documents on GRS research from 1980 to 2020. These keywords were analyzed by co-occurrence, and seven clusters were formed. These clusters are shown in
Figure 6 according to the relationship between the weights of the attributes of the links and the total link strength in different keywords.
Table 5 lists the top 30 high-frequency keywords detected in the 2692 articles, ranked by the number of occurrences in articles in which they appeared.
The top 30 keywords associated with GRS research studies associated with four variables: remote sensing (NDVI, MODIS, vegetation indexes, model, leaf-area index, time series, Landsat, reflectance, satellite); grassland ecosystems structure (vegetation, grassland, classification, biodiversity, savanna); grassland ecosystems process (dynamic, pattern, cover, variability, management, precipitation, temperature, conversation, phenology), and grassland ecosystems function (carbon, degradation, response).
Figure 6 shows the network of keywords that were selected from the total documents based on the co-occurrence method. The seven clusters of the keywords and their links were grouped, and each group was identified with a different color. The size of each cluster represents their relative contribution to the group with keywords, and the thickness of the tie line between two clusters refers to the number of interactions established between two different communities.
Table 6 shows the seven clusters that were examined. These were labeled using the keyword with the most occurrences and ranked by the percentage of keywords they included, as follows: cluster 1, red: Grassland; cluster 2, green: Biomass; cluster 3, deep blue: MODIS; cluster 4, yellow: Vegetation; cluster 5, purple: NDVI; cluster 6, light blue: Classification; cluster 7, orange: Remote sensing. The weight of the link and the total link strength contributed by each representative keyword are included, and the 10 most important keywords are provided.
Next,
Figure A1 and
Figure A2 in
Appendix A present the keywords with the most links and the highest link strength, which coincide with the terms used in the search of Web of Science to obtain the sample of 2692 articles. Therefore,
Figure A2 in
Appendix A shows 25,638 links and link strength of 1695 for the keywords “Remote Sensing” and “Vegetation”, which represent the centrality of the study, that is, the most prominent keywords in these studies. The links of five of the strongest keyword links (cluster7) were formed, during the analyzed period, with “Forest” (cluster4-430), “Landsat” (cluster7-413), “soil” (cluster1-411), “time-series” (cluster5-386), and “savanna” (4-376).
Figure A3 in
Appendix A shows the 581 links and the link strength of 2719 of the keyword “NDVI”, which represents the third keyword with the greatest number of links and total strength. The five strongest links in “NDVI” (cluster 5) were examined, namely, “Vegetation” (cluster4-476), “Remote Sensing” (cluster7-350) “Grassland” (cluster1-583), “Climate change” (cluster 5-454, “Dynamic” (cluster 5-522), and “MODIS” (cluster 5-522).
These key clusters are important forms of visualization for many studies and are highly important for understanding the current research (
Figure 6). Next, we introduce and further discuss each research area.
Grassland: During the study period, GRS research studies were focusing on resource monitoring, biodiversity protection, grassland restoration, and precise management of grassland ecosystems using remote sensing technology. The research focuses on soil physical and chemical indicators, the cycles of carbon and nitrogen chemical elements, species richness, and landscape patterns and processes. For example, the main ecological resources in the Three River Resources National Park are alpine grassland and alpine meadow. The habitat is fragile, the terrain is complex, and the grassland ecological environment is heavily degraded [
4]. GRS research provides important support for scientific management and dynamic monitoring [
56,
67,
68].
Biomass: The biomass research methods have also undergone tremendous changes from 1980 to 2020. The change in remote sensing techniques, from aerial remote sensing to satellite remote sensing [
12,
22], has achieved a significant advance in the continuity of research scales and temporal and spatial integrity, and the monitoring accuracy and timeliness have improved considerably [
28]. For the model inversion method [
18,
56], many explorations have been carried out in terms of empirical statistical methods (e.g., image processing algorithm), physical model methods (e.g., radiative transfer model, geometrical optics model), and data modeling methods (e.g., data-intensive scientific discovery, space earth observation data model) [
14]. In particular, the widespread application of model inversion methods, such as the vegetation index (NDVI) [
8,
48,
52,
67] and leaf area index (LAI) [
58,
68,
69,
70], has greatly promoted the development of grassland quantitative remote sensing [
71,
72,
73,
74]. The application of vegetation indexes [
12,
75,
76,
77] can reflect the characteristics of different ground features, such as primary productivity (or net primary productivity, NPP) [
78,
79] and coverage, and has become a research topic of grassland resources [
80].
MODIS: Since the development of satellite remote sensing technology and computer technology, the number of satellites, and the spatial and spectral resolution of the payload, have been greatly improved [
8,
12]. The ability to distinguish and recognize the details of ground features, ecological elements, and their changes, in addition to monitoring accuracy, has also been greatly enhanced. The level of quantitative remote sensing monitoring of grasslands has also been significantly improved [
8,
12]. Applications are mainly qualitative in GRS research before 2000. One of the important landmark events was that the US Earth Observation System satellite provided MODIS global quantitative remote sensing products in 2000. This enabled GRS research studies to develop more remote sensing physical models [
14]. The application of MODIS moved GRS research into the era of quantitative remote sensing [
5,
19].
Vegetation: The research area is transformed from regional to global, with a critical zone becoming a new focus. Popular research areas include South Africa, China, America, Africa, Canada, and Australia. At present, the key research area is the alpine grassland ecosystem in the Qinghai–Tibet Plateau [
71]. From 1980 to 2020, the field of GRS monitoring, and monitoring of objects, gradually expanded. The application of the field is no longer limited to monitoring grassland resources [
8,
56]. Grassland utilization, land cover change, and qualitative environmental monitoring have gradually expanded to quantitative monitoring of water, soil, and ecological parameters. As a result, significant attention has been paid to the coupling study of ecosystem structure, process, and function [
69], particularly for grassland fire and degradation monitoring [
19,
81].
NDVI: The results from 1980 to 2020 indicated that GRS research has changed from traditional pasture management to placing more emphasis on dynamic monitoring of grassland ecosystems under the conditions of disturbance due to climate change and human activities, particularly current research, which is based on grassland degradation. In recent decades, global climate change and anthropogenic activities have affected the structure and function of ecosystems, and limited sustainable development [
82,
83]. Fragility, typicality, extensiveness, and sensitivity are important characteristics of grassland ecosystems. Due to these features, NDVI is the most effective indicator to measure the response to climate change and reflect the development process of sustainability [
12,
84]. Grassland degradation is a major ecological threat [
85]. The emergence of keywords, such as phenology and time series, indicates that more attention has been paid to research into the coupling of global climate change and anthropogenic activities and other disturbances, long-term monitoring data, and quantitative inversion processes to achieve grassland degradation management [
4,
5,
35,
71,
86].
Classification: From 1980 to 2020, the selection of data sources has undergone drastic changes. Due to the development of machine learning technology [
20,
56], the applications of GRS research have greatly increased. GRS research data sources have developed from a single type of multispectral data (such as MODIS and Landsat TM) to the currently widely used hyperspectral data [
12,
87], multi-angle data [
8,
17,
74], laser radar data [
18], high-resolution data [
88], unmanned aerial vehicle (UAV) data [
89], and multi-source data. The acquisition of remote sensing data is the vital link to the quality of GRS monitoring and management research.
The acquisition of data can be roughly divided into three key categories: (1) Satellite remote sensing access to information. GRS research monitoring mainly uses satellite remote sensing data [
12], such as Landsat TM, SPOT, Landsat MSS, MODIS, and ENVISAT. It is widely used in the estimation of grassland area, monitoring of grassland growth, and remote sensing of pests and diseases. Low-resolution NOAA data is used for large-scale GRS monitoring research [
12,
90]. High-resolution satellites, such as Quick Bird, IKONOS, and Sentinel-2A [
9,
12], have been launched successively to provide powerful remote sensing information, thus ensuring that GRS research has more potential opportunities to achieve all-weather grassland monitoring, pest monitoring, etc. They play an important role in coordination with other data (such as microwave remote sensing data) to form the multi-source remote sensing data. Hyperspectral remote sensing has the characteristics of high resolution, strong band continuity, and a large amount of spectral information. It directly allows quantitative analysis of weak spectral differences in ground objects and has developed rapidly in the research of vegetation remote sensing. The use of hyperspectral reflectance data [
57] in research on the physiological characteristics of vegetation, such as grassland type identification and classification, the vegetation leaf area index, coverage and biomass estimation, and disaster assessment, has become a necessary condition for vegetation dynamic monitoring and remote sensing yield estimation. (2) Information acquisition by UAVs. Due to the rapid development of remote sensing, the global satellite positioning system, geographic information systems, microcomputers, communication equipment, and other technologies, the remote sensing technology platform of micro-UAVs has made great progress [
11,
89]. These developments have provided the technology for further development of accurate grassland management using UAVs, effectively overcoming the limitations of traditional satellite remote sensing in data acquisition [
11,
12,
89]. (3) Acquisition of integrated GRS research information from space and ground. The development of related information technologies, such as the Internet of Things, big data, and cloud computing [
11,
14,
15], provides an effective means to quickly obtain grassland ecological information for the construction of a sky–ground integrated information-acquisition technology system for GRS research.
Remote sensing: Before 2000, the key components of grassland remote sensing were atmosphere ecosystem exchange, nitrogen allocation, photosynthesis, primary productivity, glyphosate, and external interference [
52,
55,
63,
79,
91,
92]. Evapotranspiration has been the focus of grassland remote sensing research since 1980, and the word frequency is still very high. From 2002 to 2015, the key research contents were the themes soil moisture, productivity, nitrogen, carbon, water cycle process and soil recovery,
Centaurea maculosa Lam. and other invasive species monitoring and management [
64,
65,
93]. After 2016, due to the acknowledgement of global climate change and proposal of sustainable development goals 2030 [
94], GRS research has paid more attention to grassland sustainable development management, ranging from simply focusing on grassland ecological elements to monitoring and dynamic assessment of grassland ecosystem structure, function, and process [
11,
12].
3.8. Research Frontiers
The temporal evolution of cited references in GRS research is shown in
Figure 7. Using the LLR algorithm, a total of 17 visual clusters were formed, with each representing a future direction according to their activeness in
Table 7. The more active the current cluster is, the more it can represent the research frontier. In
Figure 7, the color curves represent the co-citation links added in the corresponding color year. Large nodes or nodes with red tree rings are particularly worth exploring because they are either highly referenced, have cited emergencies, or both. Based on their size from
Table 7, the clusters are numbered, with cluster #0 being the most massive cluster placed at the top of the graph. The different clusters’ timeline has different colors. As the timeline overview shows, the persistence of research content clusters is different. Some clusters last more than 15 years, while others have a relatively short lifespan. Some clusters have stayed active until 2019, the latest year for which references have been cited in this study. The clusters with the top five frequencies and activeness were selected for further analysis. The largest cluster #0 (labeled Qinghai–Tibet Plateau) containing 189 references across a 21-year period from 2007 till 2019 (
Table 7). This cluster’s silhouette (silhouette is a measure of the similarity between a node and other clusters. The value range is—1 to 1. The larger the value is, the better the node matches its cluster rather than its neighbor. If most nodes have a high silhouette value, clustering is good. As usual, a silhouette value greater than 0.5 indicates the visualization is good) value of 0.84 is the lowest among the major clusters, but this is generally considered a relatively high level of homogeneity. The most active citer to the cluster is Reinermann et al. (2020) [
21]. This paper mainly reviewed the literature on grassland production characteristics and management by satellite remote sensing, systematically describes and evaluates the existing research methods and results and reveals the spatial-temporal pattern of the existing research [
21]. The second-largest cluster #1 (labeled Qinghai–Tibet Plateau) has 144 members and a silhouette value of 0.854. The most active citer to the cluster is Pan et al. (2017). This study proposes a two-step method (1, the impact of land use change on grassland distribution; 2, the difference between the observed NDVI and the simulated NDVI based on the general linear model) to determine the contribution of climatic and non-climatic driving factors to grassland change in the Qinghai–Tibet Plateau [
95]. Although cluster #0 and cluster #1 were both labeled Qinghai–Tibet Plateau by the LLR, the research focuses were different. Cluster #0 refers to the classification and production, and cluster #0 refers to alpine grassland’s response to climate change. Unlike other clusters, these two clusters full of high impact contributions—large citation tree rings and periods of citation bursts colored in red. Since 2007, the first reference document of the cluster appeared in both clusters. Since 2010, the results of the two clusters have increased, and there are a lot of red tree rings. In the process of cluster development, many landmark documents appeared in 2010, which need to be focused on. To date, this kind of research remains active. This indicates that GRS research on Qinghai–Tibet Plateau has received increasing attention from scholars, ranging from traditional vegetation classification, dynamic monitoring, and risk assessment, to remote sensing research with grassland degradation as the core, particularly in the context of global climate change. The study of the grassland ecosystem response is a hotspot of current research. The third-largest, cluster#2 (labeled nutritive value), has 131 members and a silhouette value of 0.83. The 10-year period from 2001 through to 2010 is a highly active period of the cluster. The literature of this cluster increased from 2002 to 2009, and many articles were presented in a short period. After 2010, the cluster showed a declining trend, and the active time was up to 2012. This cluster was mainly mentioned in the mapping of grass nutrient element concentrations and vegetation index. The fourth-largest, cluster #3 (labeled southern Africa Savannah), has 103 members and a silhouette value of 0.84. Through the co-occurrence statistics of keywords, it was found that many scholars are paying attention to the grassland ecosystem dynamics in this area, mainly in response to drought climate stress, and prediction and management. The fifth-largest cluster, cluster #4 (labeled northern China), has 102 members and a silhouette value of 0.85. The grassland in northern China is mainly concentrated in Inner Mongolia. In addition to the arid climate, high grazing intensity is also an important feature of the region.
Based on the analysis of the burst literature (
Figure 8), the results indicated that the current GRS research focuses on alpine grassland in China and temperate grassland in northern China (Inner Mongolia). These studies were carried out against the background of global climate change and intensified grazing. The data sources were mostly multi-satellite remote sensing data (WorldView-2 data, satellite-derived NDVI), based on the Google Earth Engine [
96]. The research methods mainly used the Carnegie–Ames–Stanford approach based on remote sensing [
18], MODIS vegetation indexes, the random forest or random forest regression algorithm, modeling, and WorldView-2 imaging [
97,
98]. The research focused on the biophysical characteristics, phenological processes [
12,
74], and grassland management characteristics (degradation and grazing effects), and differentiated between the contributions of the influences of climate change and anthropogenic activities to NPP [
99,
100,
101,
102]. These can better predict future climate to help cope with the impact of global climate change on humans and to more quickly achieve sustainable development goals.
From the perspective of document co-citation analysis (DCA) and burst analysis, the integral results show that GRS research mainly focuses on the following three aspects:
(1) Grassland growth monitoring, including grassland coverage, productivity, and biomass [
10,
17], in addition to grassland classification [
8,
9] and area monitoring. The current monitoring methods mostly combine remote sensing data and ground-measured data and use a variety of vegetation indices to build models to estimate the growth of grasslands. This is a long-term and basic monitoring task. The results of a literature review of the research hotspots until 2020 showed that the core goals of GRS research would continue to be improving the quality of grassland ecological environment and achieving sustainable development by 2030, focusing on grassland degradation, climate change, and soil properties.
(2) Research on the process of grassland ecosystem management [
5,
16,
50,
55,
103], including grassland degradation and restoration, stocking capacity estimation, crude protein content estimation, and alien species invasion monitoring. Studies have focused on nitrogen, carbon, and water cycle processes in grassland [
4,
16,
104], and phenology is also an important research topic [
5,
8,
9,
22,
74,
105,
106]. Most of the early grassland resource research did not classify grasslands or distinguish dominant species, poisonous weeds, etc. [
93], and used the overall coverage, NPP, biomass, etc., for aims such as determining grassland degradation [
16] and estimating grass yield and rough protein content. Due to the wide application of high-resolution and hyperspectral remote sensing data, quantitative analysis of the spectral characteristics of different grassland species, and in-depth research on multi-temporal monitoring of different vegetation indices [
107,
108,
109,
110], model parameters have been continuously optimized [
11,
12,
14,
20]. These parameters can be used to effectively identify different grassland types in the community, and determine the height, coverage, and area ratio of the grassland, thus providing complete monitoring of the succession processes of grassland communities. Therefore, these works can provide more accurate scientific references for grassland degradation monitoring and restoration, stock carrying capacity assessment, and alien species invasion monitoring.
(3) Dynamic monitoring and prediction of grassland disasters, including fires, snow disasters, droughts, and insect disasters. One of the important functions of satellites is monitoring various natural disasters in large areas using, for example, high temporal and spatial resolution remote sensing and satellite radar [
8,
111]. At present, most research focuses on the causes, early warning systems, post-disaster evaluation, and recovery following fires, snow disasters, and droughts [
103,
112,
113]. Few studies have been conducted on insect disasters [
114]. Drought and fire have consistently been grassland research hotspots in arid areas [
18,
46]. By monitoring the soil water deficit of grassland and changes in grassland productivity, a grassland drought warning evaluation system can be constructed. Topography has large impacts on remote sensing, and thus GRS research, like Qinghai–Tibet Plateau, which is a huge challenge of GRS applications [
115,
116]. Furthermore, by tracking and monitoring the dynamic process of grassland fires, accurate detection of the location and scope of fires can be used to assess the area affected by the disaster, the loss of the affected biomass, and the loss of property. Due to the future development of satellite remote sensing technology, continuous improvement is inevitable in spectral band sensors, such as ground temperature and brightness. In turn, the capability for soil moisture monitoring and the spectral identification of fire spots, and the ability to prevent and reduce disasters, will continue to be strengthened. In terms of grassland pest monitoring, meter-level and sub-meter-level high-resolution remote sensing images are required to monitor the types and quantities of pests, and the level of disasters can be further determined by the difference in the spectral characteristics of the grassland before and after the disaster.