Geping Luo’s research while affiliated with State Key Laboratory of Desert and Oasis Ecology, Chinese Academy of Sciences and other places

What is this page?


This page lists works of an author who doesn't have a ResearchGate profile or hasn't added the works to their profile yet. It is automatically generated from public (personal) data to further our legitimate goal of comprehensive and accurate scientific recordkeeping. If you are this author and want this page removed, please let us know.

Publications (161)


The annual total amount of water resources and their respective proportions, annual per capita water resources, and annual runoff depth per unit area in study region. The total amount of water resources, annual per capita water resources were according to the Xinjiang Statistical Yearbook (2000–2021), the annual runoff depth per unit area for each region were according to Xinjiang Water Resources Bulletin (2010–2021) (slt.xinjiang.gov.cn/). The geospatial remote sensing data is sourced from the Geospatial Data Cloud Network of the Chinese Academy of Sciences. The data can be accessed through the platform of the Computer Network Information Center of the Chinese Academy of Sciences (https://www.gscloud.cn/).
The averaged water resources proportion in different sectors during 2000–2022 in Xinjiang, the agricultural, industrial, domestic water use and artificial ecological environment water replenishment were according to the Xinjiang Statistical Yearbook (2000–2009), Xinjiang Water Resources Bulletin (2010–2021) (https://slt.xinjiang.gov.cn/), Xinjiang Government Work Reports (2022–2023) (https://www.xinjiang.gov.cn/).
The changes of water supply and agricultural water use in Xinjiang from 2000 to 2023.
The proportions of agricultural water use in the total water supply from 2000 to 2023.
Water use by the agriculture and other sectors in 2012 and 2019.
Research on water supply and agricultural water use forecasting in arid regions: a case study of Xinjiang
  • Article
  • Full-text available

April 2025

·

13 Reads

Yue Yao

·

Chi Zhang

·

Geping Luo

·

Tao Lin

Water resources are the lifelines of the agricultural development in Xinjiang. Currently, the problem of water shortage for agriculture in this region is becoming increasingly severe. Against this backdrop, predicting the changing trends of water supply and agricultural water use in Xinjiang and analyzing the supply and use relationship between them are of great practical significance for ensuring the sustainable development of regional agriculture. Firstly, we conducted an in-depth analysis of the water supply and agricultural water use patterns in Xinjiang over the past two decades. Secondly, we evaluated and compared several mainstream water resource prediction models, ultimately developing a novel GM(1,1)-NN essemble model. Validation results demonstrated that this model exhibits superior accuracy in forecasting water supply and agricultural water use compared to other existing models. Finally, we utilized the newly developed GM(1,1)-NN essemble model to predict short-term water supply and agricultural water use trends in Xinjiang. Based on these findings, we proposed recommendations for water resource conservation from both technological and regional planting perspectives. The key results are as follows: (1) There are significant regional disparities in water resources in Xinjiang, primarily attributed to uneven precipitation distribution and imbalanced economic development. (2) The GM(1,1)-NN essemble model demonstrates high short-term predictive accuracy for both water supply and agricultural water use in Xinjiang. (3) According to our GM(1,1)-NN essemble model’s projections, both water supply and agricultural water use in Xinjiang are expected to exhibit a downward trend in the coming years. The reduction in agricultural water use will help allocate more water resources to non-agricultural sectors. (4) Despite these improvements, the contradiction between water shortage and the high proportion of agricultural water use (approaching to 88%) remains unresolved. Therefore, it is recommended to reduce agricultural water use through the widespread adoption of water-saving facilities and the optimization of crop planting structures across different regions.

Download

Vegetation carbon density (VCD) and soil organic carbon density (SOCD) in the Qinghai-Tibet Plateau (QTP) grasslands
The average VCD at temporal (A) and spatial (the white color in the figure represents non-grassland areas) (B) levels, and average SOCD at the temporal (C) and spatial (the white color in the figure represents non-grassland areas) (D) levels in the QTP grasslands between 1979 and 2018.
Vegetation carbon density (VCD) differences between grazing and non-grazing scenarios in the Qinghai-Tibet Plateau (QTP) grassland
Temporal dynamics in VCD (A), spatial dynamics in VCD difference (B), and relative difference (C) between grazing and non-grazing scenarios in QTP grasslands from 1979 to 2018. (The VCD difference represents the annual average difference in VCD between grazing and non-grazing scenarios over this period. The relative difference is equal to the quotient of the VCD difference divided by the VCD in the non-grazing scenario.)
Soil organic carbon density (SOCD) differences between grazing and non-grazing scenarios in the Qinghai-Tibet Plateau (QTP) grasslands
Temporal dynamics in SOCD (A), spatial dynamics in SOCD difference (B), and relative difference (C) between grazing and non-grazing scenarios in QTP grasslands from 1979 to 2018. (The SOCD difference represents the annual average difference in SOCD between grazing and non-grazing scenarios over this period. The relative difference is equal to the quotient of the SOCD difference divided by the SOCD in the non-grazing scenario.)
Overview of the study area
Distribution of elevation (A), yearly average intensity of grazing (the white color in the figure represents non-grassland areas) (B), yearly average temperature (the white color in the figure represents non-grassland areas) (C), and yearly average precipitation (the white color in the figure represents non-grassland areas) (D) in grasslands of the Qinghai-Tibetan Plateau between 1979 and 2018.
Validation of the model
Comparison of simulated and observed vegetation carbon density (VCD) under grazing and no-grazing scenarios (A) and soil organic carbon density (SOCD) under grazing and no-grazing scenarios (B).
Grazing decreases carbon storage in the Qinghai-Tibet Plateau grasslands

March 2025

·

95 Reads

Xiaotao Huang

·

·

Liqiong Liao

·

[...]

·

Grasslands on the Qinghai-Tibet Plateau play a crucial role in carbon sequestration and livestock farming. However, carbon storage and the environmental effects of grazing in Qinghai-Tibet Plateau grasslands are not well understood. Here, we utilised the advanced Biome-Biogeochemical Cycles with Multi-layer Soil Module model to evaluate carbon storage and responses to grazing in Qinghai-Tibet Plateau grasslands between 1979 and 2018. The average annual vegetation carbon density and soil organic carbon density were found to be 46.07 ± 7.19 gC/m² and 3,789.79 ± 17.08 gC/m², respectively. Grazing resulted in the loss of 21.63 tg of vegetation carbon, while soil organic carbon loss was 108.83 tg in 2018. Grazing was found to have reduced both vegetation carbon density and soil organic carbon density in most grasslands of the Qinghai-Tibet Plateau. The study findings highlight the extent of carbon loss caused by unreasonable grazing practices.



Characteristics of NEE across Land Cover Types (2003–2018). (a) Spatial distribution of 278 Sites. (b) Spatial patterns of annual and growing‐season NEE from 2003 to 2018. (c) Decadal differences in annual and growing‐season NEE across various land cover types.
Temporal Patterns of NEE. (a) Significant temporal trends in NEE at Sites‐LC‐NoChange. R²: Determination coefficients; RMSE: Root Mean Square Error. (b) Spatial distribution of Sites‐LC‐Changed. (c) Comparison of NEE before and after land cover change.
Environmental Controls on NEE. (a) Correlations between environmental variables and monthly NEE differences. (b) Drought effects on NEE at two southwestern cropland sites, with gray areas indicating historical drought periods. (c) Changes in NEE‐trends before and after the land cover change. Details are provided in Table S2 in Supporting Information S1.
Fine‐Scale Evaluation of Carbon Exchange Capacity in Terrestrial Ecosystems of China: Leveraging Flux Data From Meteorological Stations for Enhanced Database Representation

January 2025

·

141 Reads

Plain Language Summary Over the past two decades, China has faced increasingly frequent extreme events driven by global climate change, alongside significant changes in land cover. However, assessing the impacts of these changes on carbon exchange remains challenging due to limited observational data. This study analyzed carbon exchange dynamics in China from 2003 to 2018 using a carbon flux product from Eurasian meteorological stations. The findings revealed that, on an annual scale, forests in southwestern China exhibited the highest carbon sink capacity, while forests in central China demonstrated the strongest capacity during the growing season. Notably, carbon sink capacity significantly increased at northern forest sites located within national forest parks. Furthermore, most sites situated in China's national ecological function zones achieved enhanced carbon sink capacity following land cover changes. These results highlight the important role of site‐level assessments in supporting China's dual carbon goals. Additionally, our analysis of post‐drought carbon exchange recovery emphasizes the uncertainty introduced by the selection of recovery thresholds when evaluating drought impacts. Although the uneven distribution of sites in this carbon flux product poses challenges for regional studies, it offers valuable insights for site‐level assessments.


Bridging the gap in carbon cycle studies: Meteorological station-based carbon flux dataset as a complement to EC towers

January 2025

·

62 Reads

Agricultural and Forest Meteorology

The scarcity and uneven global distribution of eddy covariance (EC) towers are the key factors that contribute to significant uncertainties in carbon cycle studies of terrestrial ecosystems. To address this limitation of EC towers, Zhang et al. (2023b) developed a meteorological station-based net ecosystem exchange (NEE) dataset. This dataset includes 4674 global meteorological stations, representing a 22-fold increase compared to the 212 existing EC towers and covering a broader range of ecosystem types. Here, we propose a systematic framework for the comprehensive assessment of spatio-temporal representativeness and global uncertainty of the meteorological station-based carbon flux dataset. Meteorological stations effectively enhance the spatial representativeness of the EC towers and reduce the latitudinal variability of the spatial representativeness. In most regions, the temporal trends of carbon flux data from meteorological stations did not significantly differ from those observed by EC towers (p < 0.001). The global uncertainty of carbon fluxes from meteorological station is 0.37, followed by the VISIT and FLUXCOM products with uncertainties of 0.44 and 0.45, respectively. Overall, the carbon fluxes from meteorological stations exhibit higher spatial representativeness and better temporal representativeness compared to the EC tower observations and possess lower global uncertainties than the existing carbon flux gridded products. Consequently, the carbon flux data derived from meteorological stations is a trade-off dataset that addresses the low spatial representativeness of the EC towers and the high uncertainty of the gridded products. It effectively complements the existing EC tower data while ensuring accuracy. The development of this dataset will play an important role in reducing the uncertainty of global carbon sink-related studies.




Spatiotemporal patterns of warm extremes during 1981–2020
a, The frequency of warm extremes (WEF, d yr⁻¹), derived from CRUNCEP (1981–2016), ERA5 (1981–2020) and in situ observations from 3,080 GSOD (1981–2020). b, The trends in the intensity of warm extremes (WEI trend, °C yr⁻¹). c, The spatial patterns of trends in the WEF. d, The spatial patterns of trends in the WEI. The insets below c and d indicate the regions with a significance level of P < 0.05. The trend significance was tested by two-sided Student’s t-test. The numbers in the insets represent the proportion of pixels showing statistical significance. The spatial analyses (c and d) are based on ERA5 gridded climate reanalysis.
Comparisons of differences in trends of NEE between warm and non-warm extreme periods
a–d, Spatial patterns of ΔTrendNEE for NEE atmospheric inversions (Inv20 (a) and Inv13 (b)), scaled-up gridded estimations based on eddy-covariance observational data using machine learning algorithms (FLUXCOM (c)) and process-based ESM simulations (d), respectively. Trends are calculated by a 15-yr window for all datasets and ΔTrendNEE is further calculated on the basis of the average values between warm (WE) and non-warm (NonWE) extreme periods. This analysis was conducted at two different study periods, one extended period between 1981 and 2020 for the atmospheric inversions (Inv20, as shown in a) and one restricted period between 1981 and 2013 for which all NEE datasets are available (b, Inv13; c, FLUXCOM; and d, ESMs). e, Comparisons of global averaged ΔTrendNEE (three datasets for Inv20 (n = 26 × 3), Inv13 (n = 19 × 3), FLUXCOM (n = 19 × 3) and four datasets for ESMs (n = 19 × 4), respectively). Boxplots indicate mean (middle line), 25th and 75th percentiles (box), minimum and maximum (whiskers). f, Latitudinal patterns of ΔTrendNEE. The statistical tests are two-sided Student’s t-test. The inset maps below a–d and the number labelled in e indicate the number of datasets for each NEE approach tested significantly at a level of P < 0.05. The numbers in the insets represent the proportion of pixels showing statistical significance. Inset bar plots indicate contributions of ΔTrendNEE of tropical (Tro.) and non-tropical (Non-Tro.) regions to the global land.
Comparisons of differences in trends of carbon fluxes between warm and non-warm extreme periods
a,c, Spatial patterns of differences in trends of GPP between WE and NonWE periods (ΔTrendGPP) for FLUXCOM (a) and ESMs (c). b,d, Same as a (b) and c (d) but for TER (ΔTrendTER). e,f, Comparisons of global averaged trends in GPP and TER between WE and NonWE periods for FLUXCOM (e) and ESMs (f). Trends are calculated by a 15-yr window for all datasets and ΔTrendNEE is further calculated on the basis of the average values between WE and NonWE periods (three datasets for FLUXCOM (n = 19 × 3) and four datasets for ESMs (n = 19 × 4), respectively). Boxplots indicate mean (middle line), 25th and 75th percentiles (box), minimum and maximum (whiskers). The statistical tests are two-sided Student’s t-test. The insets below a–d and the number labelled in e and f indicate the number of datasets for each flux estimation approach tested significantly at a level of P < 0.05. The numbers in the insets represent the proportion of pixels showing statistical significance.
Spatial patterns of climate control on carbon fluxes during warm and non-warm extreme periods
Climate control is based on the maximum partial correlation coefficient (R) between climate variables (surface air temperature (TEMP), SM, SW and VPD) and carbon fluxes. a–c, Spatial patterns of climate control for GPP (a), TER (b) and NEE (c) during WE periods for FLUXCOM datasets. d–f, Same as a–c but for the NonWE periods. g–i, Same as a–c but for the ESM datasets. j–l, Same as d–f but for the ESM datasets. The statistical tests are two-sided Student’s t-test. The Benjamini–Hochberg approach with an FDR Padj threshold of <0.05 was used. Significant relationships (Padj < 0.05) are displayed in colours, while the non-significant ones are in grey. The numbers in maps represent the proportion of pixels showing statistical significance.
Weakening of global terrestrial carbon sequestration capacity under increasing intensity of warm extremes

November 2024

·

349 Reads

·

11 Citations

Nature Ecology & Evolution

The net ecosystem exchange (NEE), determining terrestrial carbon sequestration capacity, is strongly controlled by climate change and has exhibited substantial year-to-year fluctuations. How the increased frequency and intensity of warm extremes affect NEE variations remains unclear. Here, we combined multiple NEE datasets from atmospheric CO2 inversions, Earth system models, eddy-covariance data-driven methods and climate datasets to show that the terrestrial carbon sequestration capacity is weakened during warm extreme occurrences over the past 40 years, primarily contributed by tropical regions (81% ± 48%). The underlying mechanism can be rooted in the overwhelmingly decreased trend of gross primary productivity compared with terrestrial ecosystem respiration. Additionally, the weakened terrestrial carbon sequestration capacity is mainly driven by the transition from temperature or soil moisture control to vapour pressure deficit control, which is associated with the increasing intensity of warm extremes. Our findings suggest that warm extremes threaten the global carbon sequestration function of terrestrial ecosystems. Therefore, more attention should be given to the evolution of the increasing intensity of warm extremes in future climate projections.




Citations (75)


... Although previous studies have achieved certain progress, there are still some deficiencies. The current study mainly focuses on temperate and boreal forests, while the study on NPP simulation in subtropical forest ecosystems is biased toward short-term spatio-temporal simulation of a single forest species (e.g., bamboo forests, evergreen broadleaved forests), and there is a lack of comprehensive and in-depth long time-series spatiotemporal dynamics simulation of the productivity of different forest types in subtropical regions [19,20]. The research methods mainly rely on remote sensing data and statistical models, and relatively few simulations and mechanism studies on the internal carbon cycle processes of forest ecosystems have been carried out [21]. ...

Reference:

Spatio-Temporal Simulation of the Productivity of Four Typical Subtropical Forests: A Case Study of the Ganjiang River Basin in China
Grazing weakens the carbon sequestration capacity of dry temperate grassland ecosystems in Central Asia
  • Citing Article
  • January 2025

CATENA

... At present, NPP estimation based on MODIS data remains the mainstream method, as data with high spatiotemporal resolution (e.g., 500 m) can effectively capture the regional dynamics of vegetation. For instance, Igboeli et al. [16] used the MODIS product MOD17A3 to estimate the actual net primary productivity (ANPP) of the Lake Chad Basin (LCB) and the Aral Sea Basin (ASB) from 2000 to 2020, based on factors such as photosynthetically active radiation. They found that human activities were the dominant factor affecting ANPP in the LCB, while climate was the dominant factor in the ASB. ...

Combined impacts of land change and climate variability on ecosystem net primary productivity in arid regions
  • Citing Article
  • December 2024

Global and Planetary Change

... Land use change (LUC) profoundly affects carbon cycle processes in terrestrial ecosystems [1], serving both as a driver and outcome of climate change. The intensification of human activities, especially urbanization, agricultural expansion, and infrastructure growth, resulted in substantial changes in land use structures [2], thereby disrupting the structure and function of natural ecosystems [3].Vegetation degradation, soil erosion, and habitat fragmentation collectively weaken the carbon sink capacity of ecosystems [4], increase atmospheric carbon dioxide concentrations, and disturb the global carbon cycle [5]. ...

Weakening of global terrestrial carbon sequestration capacity under increasing intensity of warm extremes

Nature Ecology & Evolution

... The power and application potential demonstrated by machine learning in data processing has begun to be combined and applied in the environmental field in recent years, like flood risk assessment [37], thermal environment analysis [38,39], air pollutant forecasting [40], and so on. In carbon-related studies, the main focus is on carbon flux prediction [41,42]. Prăvălie et al. [43] implemented NPP modeling based on dozens of multi-machine learning techniques on a national scale for Romania by grasping the trend evolution characteristics of the NPP combined with multi-source data including remotely sensed data and inventory data. ...

Machine learning-based investigation of forest evapotranspiration, net ecosystem productivity, water use efficiency and their climate controls at meteorological station level
  • Citing Article
  • August 2024

Journal of Hydrology

... With the advancement of remote sensing technology, optical remote sensing [34], uncrewed aerial vehicle (UAV) photogrammetry [35], airborne leader, and interferometric synthetic aperture radar (InSAR) [21] have gradually become the primary methods for landslide identification and deformation monitoring [36]. In particular, the inside technology has gained significant favor in the application of large-scale landslide and glacial slide identification and deformation monitoring due to the InSAR's technical advantages [37], which include high precision [38], high resolution, extensive coverage [12,39], low cost all day, and continuous tracking of the small deformation monitoring results [40], as well as the effectiveness of the synthetic aperture radar differential interferometry in landslide [41] and glacial deformation monitoring [42]. However, it was also found that time-space decorrelation and atmospheric delay greatly influenced the deformation monitoring results [43]. ...

Monitoring Creeping Landslides with InSAR in a Loess-covered Mountainous Area in the Ili Valley, Central Asia

PFG – Journal of Photogrammetry Remote Sensing and Geoinformation Science

... Vol. XX, No. X (XXXX),[1][2][3][4][5][6][7][8][9][10][11][12][13][14][15][16][17][18] et al. an increasing trend. The results of the study show that there are differences in land changes and their drivers at different scales in the Yellow River Basin of Henan, so the overall or local ecological restoration measures concerning the Yellow River Basin should be formulated with attention to problem orientation, comprehensiveness of the measures, and pertinence. ...

Quantifying land change dynamics, resilience and feedback: A comparative analysis of the lake Chad basin in Africa and Aral Sea basin in Central Asia
  • Citing Article
  • May 2024

Journal of Environmental Management

... In world public opinion, one of the most famous areas affected by the water crisis is the Aral Sea Basin (Toderich et al., 2024). The Aral Sea basin occupies a huge area of about 1,300,000 square kilometers and covers the entirety of Uzbekistan and Tajikistan, much of Turkmenistan and Kyrgyzstan, and southern Kazakhstan. ...

Modeling and Locating the Wind Erosion at the Dry Bottom of the Aral Sea Based on an InSAR Temporal Decorrelation Decomposition Model

... According to Liu, Sun (Liu, 2019) and Wu, Zhong (Wu, 2022), drought was the proximal cause of the vegetation degradation in this area. However, the future warming of the Indian and West Pacific oceans may enhance the La Niña events that could trigger more prolonged drought events in the CA regions and threaten the sustainability of its desert ecosystems (Li, 2015;Chen, et al., 2024). Although the exact climate change effects are difficult to be quantified, given to the high uncertainty in climate and biomass data, the future studies could enhance temporal dynamics and spatial heterogeneity in seasonal vegetation water production, availability and water use efficiency at desert plant scale and related vegetation biomass and C. stocks. ...

Dryland Social-Ecological Systems in Central Asia

... Drought significantly affects the grassland ecosystem's carbon and water cycle, and the degree of this impact varies considerably across different types of grasslands [6]. The differences in the response of different grassland types to drought mainly manifest in their physiological, morphological, and ecological characteristics [9]. Drought-tolerant grasslands have a greater ability to retain and utilize water, while wet grasslands may face more severe ecological stress in times of drought [10]. ...

Drought changes the dominant water stress on the grassland and forest production in the northern hemisphere
  • Citing Article
  • February 2024

Agricultural and Forest Meteorology

... Since the 1990s, land use in Xinjiang has changed considerably, and scholars have examined change statistics from the perspectives of oases [45,46], arable land [13,27,29], and construction land [12,47] across the whole territory. Existing studies have found that the total area of artificial oases has substantially increased due to the development of agricultural technology before and after 2010, and the trend of southward movement is obvious in general [14,27]. ...

Surface deformation detection and attribution in the Mountain-Oasis-Desert Landscape in north Tianshan Mountains