Shi Yuting, Feng Yu, Wang Jinman, Bai Zhongke, Feng Xiaoming, Chen Bihui
School of Land Science and Technology, China University of Geosciences, 29 Xueyuan Road, Haidian District, 100083, Beijing, People's Republic of China.
School of Land Science and Technology, China University of Geosciences, 29 Xueyuan Road, Haidian District, 100083, Beijing, People's Republic of China; Key Laboratory of Land Consolidation and Rehabilitation, Ministry of Natural Resources, 100035, Beijing, People's Republic of China.
J Environ Manage. 2025 Jan;373:123951. doi: 10.1016/j.jenvman.2024.123951. Epub 2025 Jan 2.
Limiting adverse consequences of mining activities requires ecosystem restoration efforts, whose arrangement around mining areas is poorly designed. It is unclear, however, where best to locate ecological projects to enhance ecosystem services cost-effectively. To answer this question, we conducted an optimized ecological restoration project planning by the Resource Investment Optimization System (RIOS) model to identify the restoration priority areas in the Pingshuo Opencast Coal Mine region in Shanxi Province. This region features notable mining activity, agricultural land use, and urban development. We found that the land use changes were primarily influenced by human activities such as mining and urbanization, as well as ecological interventions from 1986 to 2022, during which the area of industrial and construction land continuously expanded. The RIOS model was configured using input data such as land use, digital elevation models (DEM), and biophysical coefficients. Ecological restoration objectives were selected, including Erosion Control for Drinking Water Quality, Erosion Control for Reservoir Maintenance, Nutrient Retention, and Baseflow. Investment optimization scenario simulations revealed that over 90% of ecological projects in the Pingshuo Opencast Coal Mine are distributed in the low-slope areas (0°-15°). Four types of technical reclamation and ecological restoration projects, i.e., agroforestry, grass strips, riparian management, and terracing, exhibit strong preferences for specific locations. Riparian management and agroforestry tend to be distributed on soil dumps; terracing and grass strips tend to be distributed in the upstream agricultural areas of rivers and junctions of watershed gullies and slopes. The model prioritized areas based on ecological restoration goals and stakeholder interests, optimizing locations that would maximize ecological benefits while addressing the objectives. Moreover, depending on the different goals of ecological restoration in the mining area, investment plans that maximize benefits for stakeholders should range between 3 and 6 million dollars. While the restoration strategies in this study were designed for the Pingshuo region, they hold potential for other mining areas with similar biophysical conditions, surrounding ecosystems, and mining scales. The RIOS model adjusts its recommendations based on specific input data, making it adaptable and broadly applicable to other mining area. The results of this study positively contribute to alleviating the conflict between ecosystem protection and socioeconomic development in mining areas, scientifically regulating ecological restoration activities, and enhancing ecosystem services. Our results provide evidence that ecological restoration interventions contribute measurably to restore the degraded ecosystems in the mining areas.
限制采矿活动的不利后果需要进行生态系统恢复工作,然而,矿区周边此类工作的安排设计欠佳。不过,尚不清楚何处是能以具有成本效益的方式提升生态系统服务的最佳生态项目选址。为回答这一问题,我们通过资源投资优化系统(RIOS)模型开展了一项优化的生态恢复项目规划,以确定山西省平朔露天煤矿区的恢复优先区域。该地区采矿活动、农业土地利用和城市发展显著。我们发现,1986年至2022年期间,土地利用变化主要受采矿和城市化等人类活动以及生态干预的影响,在此期间,工业和建设用地面积不断扩大。RIOS模型使用土地利用、数字高程模型(DEM)和生物物理系数等输入数据进行配置。选择了生态恢复目标,包括饮用水水质侵蚀控制、水库维护侵蚀控制、养分保持和基流。投资优化情景模拟显示,平朔露天煤矿90%以上的生态项目分布在低坡度区域(0°-15°)。四种类型的技术复垦和生态恢复项目,即农林业、草带、河岸管理和梯田建设,对特定位置表现出强烈偏好。河岸管理和农林业往往分布在排土场上;梯田建设和草带往往分布在河流上游的农业区域以及流域沟壑与斜坡的交汇处。该模型根据生态恢复目标和利益相关者的利益对区域进行优先排序,优化那些既能实现目标又能使生态效益最大化的位置。此外,根据矿区生态恢复的不同目标,使利益相关者效益最大化的投资计划应在300万至600万美元之间。虽然本研究中的恢复策略是针对平朔地区设计的,但它们对其他具有相似生物物理条件、周边生态系统和采矿规模的矿区具有潜在适用性。RIOS模型根据特定输入数据调整其建议,使其具有适应性并广泛适用于其他矿区。本研究结果对缓解矿区生态系统保护与社会经济发展之间的冲突、科学规范生态恢复活动以及增强生态系统服务具有积极贡献。我们的结果提供了证据,表明生态恢复干预措施对恢复矿区退化的生态系统有显著贡献。