基于树冠覆盖视角的乡村人居生态林现状评价与用地潜力分析

Using tree canopy to analyze and evaluate the state of ecological land and its potential for rural residential

  • 摘要: 林木树冠覆盖是欧美国家城乡森林生态系统评价的最常用评价指标, 与我国的林木绿化率、绿地率等指标相比, 其具有不分用地权属、导向性明显、更注重绿地质量等突出优点, 在我国目前全面推进新农村建设的新形势下, 利用该指标对农村人居林生态现状与生态发展潜力进行评估, 对于指导今后的农村生态环境保护与建设具有非常重要的理论与现实意义。本文以该指标为核心, 选择山东省安丘市凌河镇2009年7—8月25 cm分辨率的航空影像数据, 对其乡村人居生态林的结构特征、林木树冠覆盖现状以及潜在树冠覆盖分布等进行了分析。研究结果表明, 研究区现实林木树冠覆盖面积为1 088.15 hm2, 全镇的树冠覆盖率为17.12%, 99%以上为乔木冠层覆盖面积。从林木树冠覆盖的斑块粒级结构来看, 树冠覆盖斑块在面积上以巨型斑块为主, 但在数量上则以中小型斑块为主。不同行政村的树冠覆盖率评价结果显示, 全镇66个行政村中仅有24个行政村树冠覆盖率高于镇域平均水平17.12%。全镇林木树冠覆盖以中等覆盖度等级为主, 隶属此等级的行政村占行政村总数的36.36%; 其次为极低和低等覆盖度等级, 行政村所占百分比分别为21.21%、18.18%; 高等树冠覆盖度等级所占比例最少, 仅为7.58%。不同树种树冠覆盖面积的比例差异较大, 占有比例较高的树种主要有杨树、泡桐、刺槐、苹果、柿树等, 其中, 杨树的树冠覆盖比例最高, 达11.97%, 小檗最少, 不足0.01%。从未来可绿化的树冠覆盖潜力看, 研究区理论潜在树冠覆盖面积共计190.51 hm2, 占研究区总土地面积的2.91%, 包括滩涂地、裸土地、荒草地及其他未利用地等4类用地类型; 理论上全镇未来能达到的最大林木树冠覆盖率为20.12%; 扣除保障景观多样性的“10%急需律”后的实际潜力结果表明, 实际可利用的林木潜在树冠覆盖率仅2.7%, 其中以滩涂地覆盖斑块可增加的面积最多, 为59.46 hm2。总体而言, 研究区的林木树冠覆盖具有数量偏低、斑块破碎化程度高、类型单一等特点, 今后的生态建设应该保护与建设并举, 重点加强水系林网、道路林网和农田林网建设。

     

    Abstract: Tree canopy cover is the most efficient and scientific indicator for evaluating ecological construction in the world. Compared with conventional indicators (such as woody plant cover rate and percent green coverage), tree canopy cover have many outstanding advantages in ecosystem services assessment as it does not distinguish land ownership or emphasize green space quality. Under new rural construction conditions, evaluating the state and potential of village forest using tree canopy cover can more efficiently guide environmental protection and reconstruction in the countryside. Instead of urban tree canopy cover (which has been the focus of most domestic and international research), this paper investigated tree canopy cover at town level. Based on true color aerial image of Linghe Town (in a grid cell size of 25 cm × 25 cm) Shadong Province, for July and August 2009, we analyzed ecological lands in Linghe Township using existing and possible tree canopy covers as indicators. The tree canopy cover was quantitatively analyzed at the town and smaller scale such as administrative village, tree species. Statistical analysis in GIS environment showed that the investigated area was 17.12% under tree canopy cover, of which 99% was arbor tree canopy cover. Based on the area proportions of tree canopy cover of different tree species, Populus accounted for 69.92% (the highest) of the total tree canopy cover with 11.97% of canopy cover. The other dominant tree species included protecting trees of Paulownia spp., and Robinia pseudoacacia, economic trees of Malus spp., Diospyros kaki, etc. Based on the distribution of patch size of tree canopy cover, middle and small patches were dominant in terms of quantity, while large patches dominated in terms of area. The evaluation on tree canopy cover of different administrative villages indicated that among 66 villages, 24 villages’ tree canopy cover was higher than the average level of the study area (17.12%), 36.36% villages was in middle level for tree canopy cover. The proportions of villages with very low and low coverages were 21.21% and 18.18%, respectively, and that with high coverage was only 7.58%. From the standpoint of greenable land in the future, theoretically possible tree canopy cover area was 190.51 hm2, accounting for 2.91% of the study area. This included shallow land, bare land, wild grassland and other unused lands. The theoretically maximum tree canopy cover of the study area was 20.12%. However, reserving 10% of the landscape for protected diversity, the actual maximum of possible tree canopy cover was 2.7%, in which shallow land occupied the most area, 59.64 hm2. Given the distribution relationship between hydrographic network and tree canopy cover network, the river network of forest need more attention in future ecological reconstruction of countryside.

     

/

返回文章
返回