生态环境学报 ›› 2025, Vol. 34 ›› Issue (1): 4-12.DOI: 10.16258/j.cnki.1674-5906.2025.01.002

• 研究论文【生态学】 • 上一篇    下一篇

珠江三角洲城市群国土空间生态修复分区情景模拟

叶俊宏(), 刘珍环*(), 刘子瑜   

  1. 中山大学地理科学与规划学院,广东 广州 510275
  • 收稿日期:2024-08-27 出版日期:2025-01-18 发布日期:2025-01-21
  • 通讯作者: * 刘珍环。E-mail: liuzhh39@mail.sysu.edu.cn
  • 作者简介:叶俊宏(2000年生),男,硕士研究生,主要从事景观生态与土地利用研究。E-mail: yej-1@qq.com
  • 基金资助:
    广东省自然科学基金项目(2022A1515010062)

Scenarios Simulation of Territorial Space Ecological Restoration Zoning in the Pearl River Delta Urban Agglomeration Area

YE Junhong(), LIU Zhenhuan*(), LIU Ziyu   

  1. School of Geography and Planning, Sun Yat-Sen University, Guangzhou 510275, P. R. China
  • Received:2024-08-27 Online:2025-01-18 Published:2025-01-21

摘要:

当前国土空间生态修复都以现状为出发点,构建分区分类布局措施,缺少对未来情景变化的推演和预测,特别是土地利用和气候变化引起的城市生态修复区的潜在范围和强度变化还不能有效地被纳入国土空间生态修复的布局中。以珠江三角洲城市群为例,提出基于自然解决方案的生态系统退化风险—服务能力—恢复潜力的生态评价体系,设定共享社会经济路径—代表性浓度路径(SSPs-RCPs)耦合情景,用于开展国土空间生态修复分区及其未来情景方案比选。研究结果表明,1)珠江三角城市群可被划分为保护保育区、自然恢复区、辅助修复区、生态重塑区和人工重建区。其中,人工重建区呈现以“广州—东莞—深圳”为核心的连片格局,2020年占比10.8%,未来可能增长至11.7%—14.8%;生态重塑区在2020年占比约14.7%,未来情景下面积比例变化较小,主要随着城市扩张而外移。2)中期2035年,SSP119(可持续发展情景)与SSP585(常规发展情景)生态修复区的空间分布类似,SSP119优于SSP585,而SSP245(中度发展情景)最差;远期2050年,SSP119最好,SSP245次之,而SSP585生态修复需求最多。研究结论:在高度城市化地区,基于自然的解决方案的生态修复分区动态化调整以适应城市化扩张是一种较好的优先顺序布局安排。

关键词: 生态修复分区, 基于自然的解决方案, 情景模拟, 气候变化, 土地利用变化, 生态系统服务, 城市群

Abstract:

To better manage urban ecosystems and improve human well-being, the territorial space ecological restoration policy must identify priority areas and layouts for specific ecological spaces. Urban agglomerations are the most important areas where human and natural disturbances combine. Rapid changes in the urban ecosystem structure and function make it difficult for cities to maintain stable, coordinated, and sustainable ecosystem services, affecting residents’ well-being. The city faces difficulties in balancing the supply and demand of land space, and how to govern the limited ecological space plays a vital role in urban land-use strategies. Therefore, it is necessary to conduct ecosystem restoration and provide more natural ecosystem services to cities. Territorial space ecological restoration zoning is essential for prioritizing key restoration projects and layouts, as it can identify the ecosystem structure and function that need to be restored within the region. Ecological restoration zoning is usually composed of a multilevel system, mainly through top-down hierarchical divisions and classifications. The top-down approach mainly evaluates the disturbance, degradation, and destruction of ecosystems as well as the value and potential of ecological restoration, and then delineates a zoning system covering the region based on geographic patterns, dominant ecological functions, and protection and restoration goals. The bottom-up approach is based on the evolution of natural ecosystems and combines historical changes, current situation, and risk identification. Existing studies have used numerous zoning methods from the perspective of the pressure-state-response framework. However, most static zoning methods do not consider the future evolution of urban ecosystems, and there is still limited research on coupling land use and climate change to optimize ecological restoration zoning in urban areas. Thus, to identify and layout ecological restoration projects, consideration of future scenarios is still unclear. In this study, we used the Pearl River Delta urban agglomeration area as an example to simulate dynamic zoning of ecosystem restoration from the perspective of nature-based solutions. We compared the potential changes in ecosystem restoration zoning under different SSP-RCP scenarios of land use and climate change. The results showed that 1) ecosystem restoration zoning can be divided into five types: artificial reconstruction, ecological reconstruction, auxiliary ecological repair, natural recovery, and conservation areas. The proportion of conservation areas in 2020 was approximately 29.7%, with a significant decrease in the future scenarios. The proportion of natural recovery areas in 2020 is 25.8%, and except for a slight contraction in the SSP585 scenario of 2035, it will increase in future scenarios. The proportion of auxiliary repair ecological areas in 2020 was approximately 19.0%, and there will be a slight increase in future scenarios. The proportion of ecological reconstruction areas in 2020 was approximately 14.7%, and this change will be relatively small in the future. The proportion of artificial reconstruction areas in 2020 was 10.8% and there may be a slight increase in the future. 2) In the SSPs-RCP scenarios, the spatial distributions of ecological restoration zones exhibited by SSP119 and SSP585 in 2035 are similar, but SSP119 is low cost and can be restored using nature-based solutions. By 2050, SSP119 will have relatively few artificial projects. In SSP245, artificial restoration and ecological reconstruction areas decreased, whereas SSP585 showed the most severe expansion of artificial restoration and ecological reconstruction areas. Overall, the dynamic adjustment of ecological restoration zoning under nature-based solutions to adapt to urbanization is a better priority layout arrangement that can provide scientific guidance for territorial space ecological restoration planning in the Pearl River Delta urban agglomeration area.

Key words: ecological restoration zoning, nature-based solutions, scenario simulation, climate change, land use change, ecosystem services, urban agglomeration area

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