长三角地区乡村景观空间形态对植物多样性的影响

Effects of rural landscape spatial morphology on plant diversity in the Yangtze River Delta region

  • 摘要: 景观空间形态影响下的乡村植物多样性分析, 对于高质量提升乡村人居环境、稳定维持乡村生态系统及其生物多样性具有重要意义。选取江苏省南京市江宁区14个村落作为试验样区, 采用逐步回归、NMDS-Envfit等模型, 探讨了长三角乡村地区多维度景观空间形态指标对植物α多样性、β多样性的影响。结果表明: 1)乡村景观空间形态指标对植物α多样性产生了影响, 乡村半自然斑块面积比例、凝聚度、地表粗糙度、土地利用动态度等是影响长三角地区乡村植物α多样性最主要的景观空间因素。其中斑块欧式最邻近距离、斑块面积显著负向影响乔木层α多样性, 斑块破碎化和高密度道路建设对灌木层植物多样性有负作用, 土地利用动态度的增加导致了灌木层植物多样性降低, 道路距离与草本层植物多样性的负向关系突出。2)在乔木层, 地表粗糙度、半自然斑块面积比例等是β多样性的最主要影响因素; 在灌木层, 地表粗糙度、香农多样性指数为最主要的影响因素; 在草本层, 斑块面积、道路密度为最主要的影响因素。3)基于景观生态学的二维指标、三维地表度量指标对植物多样性影响最为显著, 四维景观历史动态度量指标对植物多样性影响微弱, 基于城市形态学的二维指标对植物多样性影响相对最弱。根据以上结果, 提出有效增加半自然生境面积比例和景观异质性、全面提升乡村景观凝聚度、科学维护乡村高价值林地景观、充分重视乡村历史土地利用等景观响应策略, 为乡村景观营建过程中的生物多样性维持提供参考, 并对长三角地区乡村空间规划提供了有益的量化引导。

     

    Abstract: Analyzing rural plant diversity in relation to landscape spatial morphology is necessary to improve rural living environments and maintaining stable rural ecosystems and biodiversity. Fourteen villages in Jiangning District, Nanjing City, Jiangsu Province were selected as experimental areas, and models such as stepwise regression and NMDS-Envfit were used to explore the impact of rural landscape spatial indicators on the α diversity and β diversity of rural plants in the Yangtze River Delta region. Landscape indicators included two-dimensional plane forms, three-dimensional surface features, and four-dimensional historical dynamics. The research conclusions can be summarized as follows: 1) Landscape spatial morphological indicators, such as the percentage of the landscape area covered with semi-natural patches, landscape cohesion index, surface roughness, and patch Euclidean nearest neighbor distance, had relatively significant impact on plant diversity. The patch Euclidean nearest-neighbor distance and patch area significantly and negatively affected the diversity of the arborous layer. Patch fragmentation, higher road density, and higher comprehensive dynamic degree of land use had a negative impact on the α diversity of shrub layer, while the distance from the road obviously affected the α diversity of herbaceous layer. 2) Rural landscape spatial morphological indicators had an impact on plant β diversity. Specifically, in the arborous layer, surface roughness and percentage of landscape area covered with semi-natural patches were the most important influencing factors. In the shrub layer, surface roughness and Shannon diversity index were the most important influencing factors. In the herbaceous layer, patch area and rural road density were the most important influencing factors. 3) Considering the significance of landscape indicators, landscape ecological indicators and three-dimensional surface characteristics had the most significant impact on plant diversity. The main manifestations were the positive correlation between the proportion of semi-natural patch area, patch area, cohesion degree, surface roughness, and plant diversity. The historical dynamics of the four-dimensional landscape had a weak impact on plant diversity, mainly manifesting as a positive correlation with the dynamic degree of semi-natural patches. Two-dimensional landscape indicators based on urban spatial morphology had the weakest impact on plant diversity, mainly manifesting as the negative effects of rural spatial accessibility and road density on plant diversity. Based on the above results, landscape response strategies are proposed to provide guidance for the rural landscape construction process, such as effectively increasing the proportion of semi-natural habitat areas and landscape heterogeneity, comprehensively improving rural landscape cohesion, scientifically maintaining rural high-value woodland landscapes, and fully focusing on rural historical land use. This study provides a reference for the maintenance of biodiversity during rural landscape construction and useful quantitative guidance for rural spatial planning in the Yangtze River Delta region.

     

/

返回文章
返回