CN 11-5366/S     ISSN 1673-1530
“风景园林,不只是一本期刊。”
刘颂,董宇翔,裴新生,王颖.基于NSGA-Ⅱ算法的绿色基础设施多目标空间优化[J].风景园林,2024,31(4):95-103.
引用本文: 刘颂,董宇翔,裴新生,王颖.基于NSGA-Ⅱ算法的绿色基础设施多目标空间优化[J].风景园林,2024,31(4):95-103.
LIU S, DONG Y X, PEI X S, WANG Y. Multi-objective Spatial Optimization of Green Infrastructure Based on NSGA-Ⅱ Algorithm[J]. Landscape Architecture, 2024, 31(4): 95-103.
Citation: LIU S, DONG Y X, PEI X S, WANG Y. Multi-objective Spatial Optimization of Green Infrastructure Based on NSGA-Ⅱ Algorithm[J]. Landscape Architecture, 2024, 31(4): 95-103.

基于NSGA-Ⅱ算法的绿色基础设施多目标空间优化

Multi-objective Spatial Optimization of Green Infrastructure Based on NSGA-Ⅱ Algorithm

  • 摘要:
    目的 绿色基础设施(green infrastructure, GI)是提供多种生态系统服务、保护区域生态系统安全和稳定的重要载体,而GI所能供给的各项生态系统服务之间的权衡关系导致GI的规划决策难以同时最大化多项服务供给。旨在以多项生态系统服务供给协同增益为目标构建一个辅助GI规划决策的多目标空间优化模型。
    方法 基于NSGA-Ⅱ算法,以InVEST模型构建目标函数,在Python开发了协同生境质量服务、作物生产服务、雨洪削减服务3项主导生态系统服务的GI布局优化模型,并在安徽省芜湖市中心城区进行了应用。
    结果 优化模型共获取50个末代帕累托最优GI布局,据此遴选出不同服务偏好下的GI布局方案,各方案相应服务供给能力得到显著提升:生境质量目标偏好方案的全局平均生境质量指数从现状方案的0.298 8提升至0.311 5;雨洪削减服务目标偏好方案的径流滞蓄量从70 189.34 mm/a提升至71 673.20 mm/a;作物生产目标偏好方案将作物生产总价值量从464 169.51万元提升至464 582.90万元;折衷方案的雨洪削减服务供给能力和生境质量服务供给能力优于现状方案,其径流滞蓄量和生境质量指数分别达到71 658.67 mm/a和0.299 3,而在作物生产服务供给能力上并没有实现对现状方案的提升。根据优化结果分析了GI供给的各项服务间的权衡与协同关系,归纳了在各种服务偏好下和协同多项服务时的GI空间布局特征。
    结论 多目标优化算法为辅助协同多项生态系统服务的GI布局决策、探索生态系统服务间权衡与协同关系、明确不同服务目标导向下的GI空间规划策略提供了重要参考,为国土空间规划视角下采用模型算法辅助生态空间及GI规划的实践提供了有力工具。

     

    Abstract:
    Objective Green infrastructure (GI) is an important carrier for providing diverse ecosystem services and safeguarding the security and stability of regional ecosystems. Nevertheless, the trade-off relationship between various ecosystem services that GI can provide makes it difficult for GI planning decision to simultaneously maximize multiple service provisions. This research aims to construct a multi-objective spatial optimization model for GI planning with the goal of maximizing multiple ecosystem service provisions, and to provide succinct recommendations and technical guidelines for ecological spatial and GI planning within the framework of territorial spatial planning.
    Methods Based on the NSGA-Ⅱ optimization algorithm, the GI planning optimization model for maximizing 3 ecosystem services (i.e., habitat quality, crop production, and runoff reduction) is constructed and applied to the central urban area of Wuhu, Anhui Province. The optimization model contains four parts: decision variables, constraints, objective functions, and the optimization algorithm. Decision variables determine the spatial location and type of GI, thus generating a variety of GI layout schemes, while constraints ensure that these schemes comply with certain requirements. Subsequently, the objective functions calculate the values for three critical ecosystem services, thereby representing the capacity of GI schemes to supply multiple ecosystem services. The InVEST − Crop Production Regression Model, InVEST − Habitat Quality Model, and InVEST − Urban Flood Risk Mitigation Model are used as objective functions for quantifying ecosystem services of crop production, habitat quality, and runoff reduction. The NSGA-Ⅱ algorithm can, through multiple iterations, generate GI schemes and obtain the objective function values of various ecosystem services, with the aim of maximizing multiple services and determining the optimal GI layout solution set. The research also analyzes the trade-offs and synergistic relationships among the three key ecosystem services through scatter distribution trends and curve fitting based on the optimization results. By comparing the optimal GI layout for each objective preference scheme, the optimal GI layout for each service trade-off, and the spatial layout differences of the algorithm for each GI type under the current scheme, the GI layout strategy for synergizing multiple ecosystem services in the research area is clarified.
    Results The optimization model yields a corpus of 50 Pareto-optimal planning solutions for GI. The optimized GI planning solutions demonstrate substantially improved capacity to provide ecosystem services, contingent upon differential service preferences. The compromise scheme outperforms the current scheme in providing runoff reduction service and habitat quality service, the crop production yield and habitat quality index of which reach 71,658.67 mm/a and 0.2993 respectively, while failing to achieve an upgrade in providing crop production service over the current scheme. Synthesizing the optimization findings, the trade-offs and synergies between various ecosystem services provided by GI are delineated. Further, the research proposes the spatial layout characteristics of GI under each objective preference and for synergizing multiple services, which are as follows: Under the habitat quality preference, add forest and grass space in urban areas, and decentralize the placement of habitat patches; under the crop production preference, maintain the current agricultural pattern, and increase the proportion of riverside farmland; under the rainwater runoff reduction preference, increase the storage capacity of urban areas, and construct a flood regulating network; and in the case of compromising the three services, increase the proportion of multifunctional GI, and pay attention to the composite enhancement of the services.
    Conclusion Utilizing the NSGA-Ⅱ algorithm and the InVEST model, this research innovatively develops a synergistic optimization model for GI spatial layouts. The results illuminate the trade-offs and synergies between services, which may guide the spatial planning of GI under diverse service preferences. The research demonstrates that multi-objective optimization can significantly aid in GI planning toward enhancing ecosystem service supply and informing spatial strategies. It also highlights specific GI layout characteristics for various service preference schemes, bridging the gap between ecosystem service theory and practical GI planning, and laying a foundation for future research on efficient service provision and service synergy understanding. However, this research has some limitations, particularly in its simplified modeling process due to the generality of the InVEST model and the uncertainty in data precision, potentially leading to skewed results. Future work requires refined models and high-precision data for validation. Additionally, the GI classification based on land use, layout rules, and constraints entail the enhancement of practical implementation and a deeper understanding of the ecosystem service provision mechanisms.

     

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