GIS-based Landscape Ecological Evaluation of Bamboo Forest Park-A Case Study of Yixing Bamboo Sea
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摘要: 建立在景观资源和生态环境承载力的约束条件下,探讨GIS技术在评估竹类森林公园生态修复与绿色发展的作用,为竹类森林公园挑选出适合的游憩空间,希望对竹类公园游憩空间景观保护和竹类资源的开发建设提出可行建议。在GIS技术支持下建立了宜兴竹海风景名胜区竹类景观生态评价的空间属性数据库,使用AHP法获得评价指标权重,通过栅格运算模块进行加权叠加分析,得出研究区景观视觉敏感度和生态敏感度的综合指数。结果表明:(1)通过Sa、St、Sd和Sc 4个分量合取和析取,得到宜兴竹海风景名胜区游憩空间竹林景观视觉敏感度综合评价,一级、二级、三级、四级敏感区的面积分别为2.92、11.63、243.34和220.14 hm2。(2)选择了高程、坡度、坡向、土地利用和水文生态因子进行AHP及加权叠加分析,对宜兴竹海风景名胜区游憩空间建设的生态敏感度综合评价,计算高敏感区、中敏感区、低敏感区的面积分别为174.33、228.38和75.85 hm2。由此得出:(1)一级视觉敏感区内要避免任何干扰或破坏景观的建设活动。二级视觉敏感区营造优美的竹林景观及人文景观,形成良好的景观生态环境。三级视觉敏感区为建设竹林康养空间、康养游步道、康养休息区域等开发活动提供依据。四级视觉敏感区构成了竹类公园优质的竹林风光资源,应好好保护。(2)一级生态高敏感区以维持竹类公园生态平衡为主。二级生态中敏感区开展以“气候性地形疗法”+“环境疗法即‘竹林环境+竹林漫步’”模式的竹林康养活动。三级生态低敏感区可考虑集中建设竹林游憩配套设施,但建筑风貌要协调周围环境。(3)以竹林利用为目的进入各类竹类风景名胜区的旅游活动,需注意生态环境容量对人为活动的约束条件,维持竹类公园竹林生态系统调节功能。Abstract: This paper aims to explore the role of GIS technology in evaluating the ecological restoration and green development of bamboo forest parks under the constraints of landscape resources and ecological environment carrying capacity, and to select suitable recreation space for bamboo forest parks. It is hoped to put forward some suggestions for the landscape protection of bamboo park recreation space and the development and construction of bamboo resources. With the support of GIS technology, the spatial attribute database of bamboo landscape ecological evaluation index in Yixing Bamboo Sea Scenic Spot was established, the weight of evaluation index was obtained by AHP method, and the weighted overlay analysis was carried out by grid operation module. Through the combination and extraction of four components of Sa, St, Sd and Sc, the comprehensive evaluation of visual sensitivity of bamboo landscape in the recreation space of Yixing Bamboo Sea was obtained. The areas of the first, second, third and fourth grade sensitive areas were 2.92 hm2, 11.63 hm2, 243.34 hm2 and 220.14 hm2, respectively. Five factors, i.e., elevation, slope, aspect, land use and hydrology, were selected for AHP and weighted overlay analysis to evaluate the ecological sensitivity of recreation space construction in Yixing Bamboo Sea. The areas of high, middle and low sensitive areas are 174.33 hm2, 228.38 hm2 and 75.85 hm2 respectively. Any construction activities that may interfere with or destroy the landscape should be avoided in the first-level visual sensitive area. In the secondary visual sensitive area, it is suitable to create beautiful bamboo forest landscape and cultural landscape, and form a good landscape ecological environment. The third-level visual sensitive area may provide a basis for the construction of bamboo forest recreation space, path, and rest area and other development activities. The fourth-level visual sensitive area forms the high-quality bamboo scenery resources in the forest park, which should be well protected. The highly sensitive area is mainly to maintain the ecological balance of bamboo parks. In the middle sensitive areas, it is suitable for carrying out rehabilitation activities in the mode of climatic topography therapy + environmental therapy, that is, walking in the bamboo forest. In the low sensitive areas, centralized construction of bamboo forest recreation facilities can be considered, but the architectural style should be coordinated with the surrounding environment. For tourist activities entering various bamboo scenic spots, attention should be paid to the constraints of eco-environmental capacity on human activities and to maintain the adjustment ability and cultural function of bamboo park ecosystem.
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[1] 兰思仁.森林景观计量评价与福建森林景观的开发应用研究综述[J].华东森林经理,2001(4):42,53-57. [2] 蔡碧凡.竹类旅游资源的分类与评价体系构建[J].竹子研究汇刊,2011,30(3):37-42. [3] 朱东国,谢炳庚,陈永林.基于生态敏感性评价的山地旅游城市旅游用地策略——以张家界市为例[J].经济地理,2015,35(6):184-189. [4] 覃婕,周志翔,滕明君,等.武汉市九峰城市森林保护区景观敏感度评价[J].长江流域资源与环境,2009,18(5):453-458. [5] 鲁敏,孔亚菲.生态敏感性评价研究进展[J].山东建筑大学学报,2014,29(4):347-352. [6] 徐君,李贵芳,王育红.生态脆弱性国内外研究综述与展望[J].华东经济管理,2016,30(4):149-162. [7] 李雪莹,齐童,张国庆,等.国内外视觉景观影响评价综述[J].首都师范大学学报(自然科学版),2017,38(5):62-69. [8] 王云才.论都市郊区游憩景观规划与景观生态保护——以北京市郊区游憩景观规划为例[J].地理研究,2003(3):324-334. [9] 保罗·戈比斯特,杭迪.西方生态美学的进展:从景观感知与评估的视角看[J].学术研究,2010(4):2-14,159. [10] 肖笃宁,解伏菊,魏建兵.景观价值与景观保护评价[J].地理科学,2006(4):4506-4512. [11] 莫美颖,邓华锋.福建洪田村森林景观视觉敏感度评价[J].西北林学院学报,2020,35(1):232-238. [12] 陈利顶,李秀珍,傅伯杰,等.中国景观生态学发展历程与未来研究重点[J].生态学报,2014,34(12):3129-3141. [13] 彭建,党威雄,刘焱序,等.景观生态风险评价研究进展与展望[J].地理学报,2015,70(4):664-677. [14] 曹祺文,张曦文,马洪坤,等.景观生态风险研究进展及基于生态系统服务的评价框架:ESRISK[J].地理学报,2018,73(5):843-855. [15] 常青,苏王新,王宏.景观生态学在风景园林领域应用的研究进展[J].应用生态学报,2019,30(11):3991-4002. [16] 冯一凡,赵鸣.基于生境营造的北京城市边缘区绿色空间营建策略研究[J].北京规划建设,2019(5):106-110. [17] 杨洋,黄少伟,唐洪辉.景观评价研究进展[J].林业与环境科学,2018,34(1):116-122. [18] 丁桂生.森林风景区景观生态规划研究现状与展望[J].中国林副特产,2011(1):88-92. [19] 章戈,严力蛟.森林风景区景观生态规划研究现状与展望[J].林业科学,2009,45(1):144-151. [20] 刘是亨,王欣,胡杜娟,等.基于序关系分析法的武夷山国家公园生态敏感性评价[J].江西科学,2021,39(1):63-69. [21] 张娇. 基于GIS的宜兴竹海森林公园旅游开发生态适宜性评价研究[D].南京:南京大学,2016. [22] 刘增贤,高峻.景观空间感知评价的GIS方法应用研究[J].测绘与空间地理信息,2012,35(7):58-62. [23] 谭人华,王艳慧,关鸿亮.基于GIS与模糊层次分析法的景观视觉资源综合评价[J].地球信息科学学报,2019,21(5):663-674. [24] 章侃丰,角媛梅,刘歆,等.基于敏感度-主观偏好矩阵的哈尼梯田视觉景观关键区识别[J].生态学报,2018,38(10):3661-3672. [25] 齐津达,傅伟聪,李炜,等.基于GIS与SBE法的旗山国家森林公园景观视觉评价[J].西北林学院学报,2015,30(2):245-250. [26] 肖伟峰,张婷婷.基于视觉分析的百色市麒麟山公园景观要素评价与布局优化[J].规划师,2016,32(4):78-84. [27] 俞孔坚.景观敏感度与阀值评价研究[J].地理研究,1991(2):38-51. [28] 刘平,周星宇,胡冬冬.青藏高原然乌旅游景区空间评价模型研究[J].规划师,2019,35(6):16-20. [29] 王宝川,刘晨,田孟良.应用层次分析法和地理信息系统技术对四川杜仲适宜栽培区区划[J].东北林业大学学报,2020,48(9):20-25. [30] 高炎冰,陶洪波,张玉娇,等.哈尔滨市曙光滨水公园的生态敏感性分析[J].北方园艺,2019(16):90-97. [31] 贺征兵,徐瑶,李雁杰.基于GIS的黄龙核桃生态气候适宜性评价研究[J].北方园艺,2020(15):89-95. [32] 邱正游.基于GIS的视觉景观影响定量评价方法研究[J].安阳师范学院学报,2019(2):90-93. [33] 李婷婷,陈露,赵锦慧.RS与GIS技术在我国城市绿地研究中的应用[J].中国城市林业,2015,13(4):10-13. [34] 陈丹,彭蓉.台湾地区国家公园环境教育体系浅析——以金门国家公园为例[J].林产工业,2019,46(5):62-64. [35] 戚艳伟.森林特色小镇规划研究[J].林产工业,2019,56(11):68-70. [36] 付尧,尹晶萍,刘晓波.现代木结构建筑在森林公园中的应用研究[J].林产工业,2020,57(4):55-57.
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