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Response of the Desertification Landscape Patterns to Spatial–Temporal Changes of Land Use: A Case Study of Salaxi in South China Karst

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  • Tian Shu

    (School of Karst Science, Guizhou Engineering Laboratory for Karst Desertification Control and Eco-Industry, Guizhou Normal University, Guiyang 550001, China
    State Engineering Technology Institute for Karst Desertification Control, Guiyang 550001, China
    Guizhou Institute of Agricultural Science and Technology Information, Guiyang 550006, China)

  • Kangning Xiong

    (School of Karst Science, Guizhou Engineering Laboratory for Karst Desertification Control and Eco-Industry, Guizhou Normal University, Guiyang 550001, China
    State Engineering Technology Institute for Karst Desertification Control, Guiyang 550001, China)

  • Ning Zhang

    (School of Karst Science, Guizhou Engineering Laboratory for Karst Desertification Control and Eco-Industry, Guizhou Normal University, Guiyang 550001, China
    State Engineering Technology Institute for Karst Desertification Control, Guiyang 550001, China)

Abstract

Land use change and karst desertification (KD) are interdependent. It is crucial to investigate the relationship between the KD landscape and spatial–temporal changes in land use for effective and sustainable KD management practices in karst plateau mountains. In this study, we analyzed the spatial and temporal characteristics, evolution in the pattern of land use, and KD in the Salaxi study area from 2009 to 2019, using the landscape pattern index and KD evolution trajectories, and discussed their response relationships. The results revealed the following: (1) In Salaxi, cultivated land predominantly transformed into shrubland, grassland, and woodland. The area of grassland, construction land, and garden land significantly increased, with respective increments of 379.85%, 157.14%, and 1847.81%. Conversely, the area of unutilized land decreased from 53.56 hm 2 to 8.55 hm 2 , with the proportion declining from 0.62% to 0.10%. KD primarily occurs in shrubland, cultivated land, and woodland. (2) The areas of non-KD and potential KD have increased. There was a noticeable conversion of light and medium KD into potential KD, with areas of 1206.84 hm 2 and 459.47 hm 2 , respectively. The KD landscape is dominated by stable and weakening ecological restoration. The comprehensive ranking of the incidence of soil KD in the study area is as follows: yellow soil > yellow-brown soil > coarse bone soil > limestone soil > purple soil. (3) The land use landscape index, the evenness index, and the fragmentation index in the demonstration area increased by 0.263, 0.120, and 0.534, respectively, while the KD landscape index, evenness index, and fragmentation index decreased by 0.360, 0.123, and 1.098, respectively. Additionally, the spreading index and aggregation index of the land use landscape decreased by 9.247 and 3.086, respectively, while the KD landscape’s spreading index and aggregation index increased by 6.688 and 0.430, respectively. Both the sub-dimension indexes of the land use landscape and the KD landscape increased by 0.009. Overall, the landscape pattern of KD changes in response to land use variations and different land types exhibited varying responses to KD. The study of KD and land use landscape patterns can provide references for national strategies on KD control and the development of ecological industries.

Suggested Citation

  • Tian Shu & Kangning Xiong & Ning Zhang, 2023. "Response of the Desertification Landscape Patterns to Spatial–Temporal Changes of Land Use: A Case Study of Salaxi in South China Karst," Land, MDPI, vol. 12(8), pages 1-17, August.
  • Handle: RePEc:gam:jlands:v:12:y:2023:i:8:p:1557-:d:1211401
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    References listed on IDEAS

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    1. Daniela Ribeiro & Matija Zorn, 2021. "Sustainability and Slovenian Karst Landscapes: Evaluation of a Low Karst Plain," Sustainability, MDPI, vol. 13(4), pages 1-22, February.
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    Cited by:

    1. Weiyi Lu & Geer Teni & Huishi Du, 2024. "Vegetation–Lake–Sand Landscape of Northeast China Sandy Land between 1980 and 2022: Pattern, Evolution, and Driving Forces," Sustainability, MDPI, vol. 16(8), pages 1-18, April.
    2. Ning Zhang & Yongkuan Chi, 2023. "20-Year Ecological Impact Analysis of Shibing Karst World Natural Heritage through Land Use," Land, MDPI, vol. 12(11), pages 1-12, October.

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