
生物多样性 ›› 2009, Vol. 17 ›› Issue (1): 10-18. DOI: 10.3724/SP.J.1003.2009.08225 cstr: 32101.14.SP.J.1003.2009.08225
收稿日期:2008-09-10
接受日期:2009-01-06
出版日期:2009-01-20
发布日期:2009-01-20
通讯作者:
欧阳志云
作者简介:* E-mail: zyouyang@rcees.ac.cn基金资助:
Xuezhi Wang, Weihua Xu, Zhiyun Ouyang*(
)
Received:2008-09-10
Accepted:2009-01-06
Online:2009-01-20
Published:2009-01-20
Contact:
Zhiyun Ouyang
摘要:
岷山中部地区是我国野生大熊猫(Ailuropoda melanoleuca)种群分布密度较高的地区之一, 但近年来砍伐森林、种植药材等农业活动较为突出, 可能对大熊猫及其生境利用造成不利影响。为了明确该地区农用地的时空变化特征, 及其对保护区内外大熊猫生境的影响, 我们采用遥感影像解析、GIS空间分析和野外调查相结合的方法在白草河流域进行了本项研究。结果表明, 该流域的农用地主要分布在海拔1,700 m以下的地区。从1994-2008年, 农用地面积呈现先减少后增加的趋势: 1994-2001年间, 农用地面积减少, 减少区域主要在海拔1,700 m以下的地区; 2001-2008年间, 农用地面积增加明显, 增加区域主要在海拔1,700 m以上的高海拔地区和自然保护区周边。农用地扩张直接导致1994-2008年间该地区5,281 hm2 (6.46%) 的大熊猫生境丧失。就保护区内外而言, 保护区外部大熊猫生境的丧失比例达21.53%, 而保护区内部的生境变化不大。为了有效保护该地区的大熊猫生境, 除了禁止在自然保护区内部进行开发外, 建议对保护区外部的大熊猫生境进行保护, 禁止在海拔1,700 m以上的高海拔地区进行土地开发。
王学志, 徐卫华, 欧阳志云 (2009) 农用地时空变化对大熊猫生境的影响:以岷山中部地区的白草河流域为例. 生物多样性, 17, 10-18. DOI: 10.3724/SP.J.1003.2009.08225.
Xuezhi Wang, Weihua Xu, Zhiyun Ouyang (2009) Impacts of spatio-temporal changes in agricultural land on giant panda habitat: A case study in the Baicaohe watershed of the mid-Minshan Mountains. Biodiversity Science, 17, 10-18. DOI: 10.3724/SP.J.1003.2009.08225.
| 自然因子 Natural factors | 适宜 Suitable | 次适宜 Marginally suitable | 不适宜 Unsuitable | |||||
|---|---|---|---|---|---|---|---|---|
| 标准 Criteria | 痕迹点比例 Ratio to total fecal samples (%) | 标准 Criteria | 痕迹点比例 Ratio to total fecal samples (%) | 标准 Criteria | 痕迹点比例 Ratio to total fecal samples (%) | |||
| 海拔 Elevation (m) | 2,000-3,100 | 92.20 | 1,700-2,000; 3,100-3,500 | 7.80 | <1,700; ≥3,500 | 0 | ||
| 坡度 Slope (°) | ≤40 | 81.93 | 40-50 | 18.07 | >50 | 0 | ||
| 植被类型 Vegetation | 森林 Forest | 97.54 | 灌丛 Shrubs | 2.46 | 其他类型 Others | 0 | ||
| 竹类 Bamboos | 有 Presence | 97.33 | 无 Absence | 2.67 | ||||
表1 自然因子对大熊猫生境影响的评价标准
Table 1 Assessment of natural factors used to determine habitat suitability for giant pandas
| 自然因子 Natural factors | 适宜 Suitable | 次适宜 Marginally suitable | 不适宜 Unsuitable | |||||
|---|---|---|---|---|---|---|---|---|
| 标准 Criteria | 痕迹点比例 Ratio to total fecal samples (%) | 标准 Criteria | 痕迹点比例 Ratio to total fecal samples (%) | 标准 Criteria | 痕迹点比例 Ratio to total fecal samples (%) | |||
| 海拔 Elevation (m) | 2,000-3,100 | 92.20 | 1,700-2,000; 3,100-3,500 | 7.80 | <1,700; ≥3,500 | 0 | ||
| 坡度 Slope (°) | ≤40 | 81.93 | 40-50 | 18.07 | >50 | 0 | ||
| 植被类型 Vegetation | 森林 Forest | 97.54 | 灌丛 Shrubs | 2.46 | 其他类型 Others | 0 | ||
| 竹类 Bamboos | 有 Presence | 97.33 | 无 Absence | 2.67 | ||||
| 人为干扰因子 Human factors | 强 Strong | 中等 Moderate | 弱 Weak | 无 None | |||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| 距离 Distance (m) | 痕迹点比例 Ratio to total samples (%) | 距离 Distance (m) | 痕迹点比例 Ratio to total samples (%) | 距离Distance (m) | 痕迹点比例 Ratio to total samples (%) | 距离Distance (m) | 痕迹点比例 Ratio to total samples (%) | ||||
| 公路距离 Distance to roads | 0-100 | 0.0 | 100-300 | 2.2 | 300-700 | 6.6 | >700 | 91.2 | |||
| 居民点距离 Distance to human settlements | 0-700 | 0.0 | 700-900 | 3.5 | 900-1,400 | 5.3 | >1,400 | 91.2 | |||
| 农用地距离 Distance to agricultural land | 0-100 | 0.8 | 100-400 | 3.8 | 400-700 | 6.0 | >700 | 89.5 | |||
表2 人类活动干扰对大熊猫生境影响的评价标准
Table 2 Assessment of the effects of human factors on giant panda habitat
| 人为干扰因子 Human factors | 强 Strong | 中等 Moderate | 弱 Weak | 无 None | |||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| 距离 Distance (m) | 痕迹点比例 Ratio to total samples (%) | 距离 Distance (m) | 痕迹点比例 Ratio to total samples (%) | 距离Distance (m) | 痕迹点比例 Ratio to total samples (%) | 距离Distance (m) | 痕迹点比例 Ratio to total samples (%) | ||||
| 公路距离 Distance to roads | 0-100 | 0.0 | 100-300 | 2.2 | 300-700 | 6.6 | >700 | 91.2 | |||
| 居民点距离 Distance to human settlements | 0-700 | 0.0 | 700-900 | 3.5 | 900-1,400 | 5.3 | >1,400 | 91.2 | |||
| 农用地距离 Distance to agricultural land | 0-100 | 0.8 | 100-400 | 3.8 | 400-700 | 6.0 | >700 | 89.5 | |||
| 实际生境质量 人为影响强度 Degree of Quality of actual habitat human influences 潜在生境 质量 Quality of potential habitat | 强 Strong | 中 Moderate | 弱 Weak | 无 None |
|---|---|---|---|---|
| 适宜 Suitable | 不适宜 Unsuitable | 次适宜 Marginally suitable | 次适宜 Marginally suitable | 适宜 Suitable |
| 次适宜 Marginally suitable | 不适宜 Unsuitable | 不适宜 Unsuitable | 次适宜 Marginally suitable | 次适宜 Marginally suitable |
| 不适宜 Unsuitable | 不适宜 Unsuitable | 不适宜 Unsuitable | 不适宜 Unsuitable | 不适宜 Unsuitable |
表3 人类活动影响等级与大熊猫潜在生境的组合矩阵
Table 3 Realized habitat resulting from a combination of potential habitat and human effects on habitat
| 实际生境质量 人为影响强度 Degree of Quality of actual habitat human influences 潜在生境 质量 Quality of potential habitat | 强 Strong | 中 Moderate | 弱 Weak | 无 None |
|---|---|---|---|---|
| 适宜 Suitable | 不适宜 Unsuitable | 次适宜 Marginally suitable | 次适宜 Marginally suitable | 适宜 Suitable |
| 次适宜 Marginally suitable | 不适宜 Unsuitable | 不适宜 Unsuitable | 次适宜 Marginally suitable | 次适宜 Marginally suitable |
| 不适宜 Unsuitable | 不适宜 Unsuitable | 不适宜 Unsuitable | 不适宜 Unsuitable | 不适宜 Unsuitable |
图4 白草河流域距自然保护区不同距离内的农用地面积(到保护区距离为0表示位于自然保护区内)
Fig. 4 Agricultural land areas around the reserves in Baicaohe watershed. Distance “0” indicates the regions inside the reserves.
| 1994 | 2001 | 2008 | |||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| 次适宜 Marginally suitable | 适宜 Suitable | 总计 Total | 次适宜 Marginally suitable | 适宜 Suitable | 总计 Total | 次适宜 Marginally suitable | 适宜 Suitable | 总计 Total | |||
| 自然保护区外 Outside reserves | 10,160 | 8,200 | 18,360 | 9,157 | 7,821 | 16,978 | 8,527 | 5,880 | 14,407 | ||
| 自然保护区内 Inside reserves | 32,740 | 30,614 | 63,354 | 32,426 | 30,448 | 62,874 | 33,242 | 28,785 | 62,026 | ||
| 总计 Total | 42,900 | 38,814 | 81,714 | 41,584 | 38,269 | 79,852 | 41,769 | 34,664 | 76,433 | ||
表4 白草河流域各年大熊猫生境面积(hm2)
Table 4 The habitat area (hm2) of giant panda in Baicaohe watershed in 1994, 2001 and 2008
| 1994 | 2001 | 2008 | |||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| 次适宜 Marginally suitable | 适宜 Suitable | 总计 Total | 次适宜 Marginally suitable | 适宜 Suitable | 总计 Total | 次适宜 Marginally suitable | 适宜 Suitable | 总计 Total | |||
| 自然保护区外 Outside reserves | 10,160 | 8,200 | 18,360 | 9,157 | 7,821 | 16,978 | 8,527 | 5,880 | 14,407 | ||
| 自然保护区内 Inside reserves | 32,740 | 30,614 | 63,354 | 32,426 | 30,448 | 62,874 | 33,242 | 28,785 | 62,026 | ||
| 总计 Total | 42,900 | 38,814 | 81,714 | 41,584 | 38,269 | 79,852 | 41,769 | 34,664 | 76,433 | ||
| 海拔 Elevation | 潜在生境丧失面积 Potential habitat decreased (hm2) | 生境破坏面积 Damaged habitat by agricultural land (hm2) | 生境影响面积 Influenced habitat by agricultural land (hm2) | ||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| 1994 | 2001 | 2008 | 1994 | 2001 | 2008 | 1994 | 2001 | 2008 | |||
| 1,700-1,800 | 2,332 | 2,452 | 2,729 | 162 | 185 | 437 | 2,009 | 2,101 | 2,156 | ||
| 1,800-1,900 | 1,636 | 1,917 | 2,376 | 57 | 105 | 405 | 1,450 | 1,677 | 1,857 | ||
| 1,900-2,000 | 872 | 1,279 | 1,885 | 15 | 30 | 330 | 756 | 1,158 | 1,459 | ||
| 2,000-2,100 | 450 | 611 | 1,258 | 11 | 37 | 281 | 317 | 464 | 849 | ||
| 2,100-2,200 | 305 | 433 | 920 | 12 | 24 | 176 | 161 | 290 | 590 | ||
| 2,200-2,300 | 212 | 317 | 647 | 7 | 20 | 84 | 107 | 233 | 441 | ||
| 2,300-2,400 | 121 | 200 | 441 | 1 | 3 | 52 | 61 | 158 | 278 | ||
| 2,400-2,500 | 77 | 99 | 336 | 0 | 3 | 30 | 25 | 79 | 171 | ||
| 合计 Total | 6,005 | 7,308 | 10,592 | 265 | 407 | 1,795 | 4,886 | 6,160 | 7,801 | ||
表5 农用地变化对大熊猫生境的影响
Table 5 The influence area of agricultural land on giant panda habitat in 1994, 2001 and 2008
| 海拔 Elevation | 潜在生境丧失面积 Potential habitat decreased (hm2) | 生境破坏面积 Damaged habitat by agricultural land (hm2) | 生境影响面积 Influenced habitat by agricultural land (hm2) | ||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| 1994 | 2001 | 2008 | 1994 | 2001 | 2008 | 1994 | 2001 | 2008 | |||
| 1,700-1,800 | 2,332 | 2,452 | 2,729 | 162 | 185 | 437 | 2,009 | 2,101 | 2,156 | ||
| 1,800-1,900 | 1,636 | 1,917 | 2,376 | 57 | 105 | 405 | 1,450 | 1,677 | 1,857 | ||
| 1,900-2,000 | 872 | 1,279 | 1,885 | 15 | 30 | 330 | 756 | 1,158 | 1,459 | ||
| 2,000-2,100 | 450 | 611 | 1,258 | 11 | 37 | 281 | 317 | 464 | 849 | ||
| 2,100-2,200 | 305 | 433 | 920 | 12 | 24 | 176 | 161 | 290 | 590 | ||
| 2,200-2,300 | 212 | 317 | 647 | 7 | 20 | 84 | 107 | 233 | 441 | ||
| 2,300-2,400 | 121 | 200 | 441 | 1 | 3 | 52 | 61 | 158 | 278 | ||
| 2,400-2,500 | 77 | 99 | 336 | 0 | 3 | 30 | 25 | 79 | 171 | ||
| 合计 Total | 6,005 | 7,308 | 10,592 | 265 | 407 | 1,795 | 4,886 | 6,160 | 7,801 | ||
| [1] | DeFries R, Hansen A, Newton AC, Hansen MC (2005) Increasing isolation of protected areas in tropical forests over the past twenty years. Ecological Applications, 15, 19-26. |
| [2] |
DeFries R, Hansen A, Turner BL, Reid R, Liu JG (2007) Land use change around protected areas: management to balance human needs and ecological function. Ecological Applications, 17, 1031-1038.
URL PMID |
| [3] | Hansen AJ, Rasker R, Maxwell B, Rotella JJ, Johnson JD, Parmenter AW, Langner U, Cohen WB, Lawrence RL, Kraska MPV (2002) Ecological causes and consequences of demographic change in the New West. BioScience, 52, 151-162. |
| [4] |
Hansen AJ, DeFries R (2007) Ecological mechanisms linking protected areas to surrounding lands. Ecological Applications, 17, 974-988.
URL PMID |
| [5] | Linderman M, Bearer S, An L, Tan YC, Ouyang ZY, Liu JG (2005) The effects of understory bamboo on broad-scale estimates of giant panda habitat. Biological Conservation, 121, 383-390. |
| [6] | Liu JG, Ouyang ZY, Taylor WW, Groop R, Tan YC, Zhang HM (1999) A framework for evaluating the effects of human factors on wildlife habitat: the case of giant pandas. Conservation Biology, 13, 1360-1370. |
| [7] | Liu JG, Linderman M, Ouyang ZY, An L, Yang J, Zhang HM (2001) Ecological degradation in protected areas: the case of Wolong Nature Reserve for giant pandas. Science, 292, 98-101. |
| [8] | Liu XH (2001) Mapping and Modelling the Habitat of Giant Pandas in Foping Nature Reserve, China. Printer: Febodruk BV, Enschede, the Netherlands. |
| [9] | Ouyang ZY (欧阳志云), Liu JG (刘建国), Xiao H (肖寒), Tan YC (谭迎春), Zhang HM (张和民) (2001) An assessment of giant panda habitat in Wolong Nature Reserve. Acta Ecologica Sinica (生态学报), 21, 1869-1874. (in Chinese with English abstract) |
| [10] | Serneels S, Lambin EL (2001) Proximate causes of land-use change in Narok district, Kenya: a spatial statistical model. Agriculture, Ecosystems & Environment, 85, 65-81. |
| [11] | State Forestry Administration (国家林业局) (2006) The Third National Survey Report on Giant Panda in China (全国第三次大熊猫调查报告). Science Press, Beijing. (in Chinese) |
| [12] | Taylor AH, Qin ZS (1993) Bamboo regeneration after flowering in the Wolong Giant Panda Reserve, China. Biological Conservation, 63, 231-234. |
| [13] | Viňa A, Bearer S, Chen XD, He GM, Linderman M, An L, Zhang HM, Ouyang ZY, Liu JG (2007) Temporal changes in giant panda habitat connectivity across boundaries of Wolong Nature Reserve, China. Ecological Applications, 17, 1019-1030. |
| [14] | Wang XZ (王学志), Xu WH (徐卫华), Ouyang ZY (欧阳志云), Liu JG (刘建国), Xiao Y (肖燚), Chen YP (陈佑平), Zhao LJ (赵联军), Huang JZ (黄俊忠)(2008) Application of ecological-niche factor analysis in habitat assessment of giant pandas. Acta Ecologica Sinica (生态学报), 28, 821-828. (in Chinese with English abstract) |
| [15] | Xiao Y (肖燚), Ouyang ZY (欧阳志云), Zhu CQ (朱春全), Zhao JZ (赵景柱), He GJ (何国金), Wang XK (王效科) (2004) An assessment of giant panda habitat in Minshan, Sichuan, China. Acta Ecologica Sinica (生态学报), 24, 1373-1379. (in Chinese with English abstract) |
| [16] | Xu WH (徐卫华), Ouyang ZY (欧阳志云), Jiang ZY (蒋泽银), Zheng H (郑华), Liu JG (刘建国)(2006) Assessment of giant panda habitat in the Daxiangling Mountain Range, Sichuan, China. Biodiversity Science (生物多样性), 14, 223-231. (in Chinese with English abstract) |
| [17] | Xu WH, Ouyang ZY, Viňa A, Zheng H, Liu JG, Xiao Y (2006) Designing a conservation plan for protecting the habitat for giant pandas in the Qionglai Mountain range, China. Diversity and Distributions, 12, 610-619. |
| [18] | Zhang WG (张文广), Tang ZH (唐中海), Qi DW (齐敦武), Hu YM (胡远满), Hu JC (胡锦矗) (2007) Habitat assessment for giant pandas (Ailuropoda melanoleuca) on the northern slope of the Daxiangling Mountains. Acta Theriologica Sinica (兽类学报), 27, 146-152. (in Chinese with English abstract) |
| [1] | 张同, 梁力文, 王长剑, 舒服, 王璐, 郭泽光, 卓玛曲珍, 钱芊, 蒋安莉, 敖俊杰, 彭兴文, 伍小刚, 向左甫, 郭克疾, 廖梓延. 基于红外相机的西藏芒康滇金丝猴国家级自然保护区鸟兽多样性及代表性物种的季节性空间利用特征[J]. 生物多样性, 2026, 34(4): 25435-. |
| [2] | 蒋翠憶, 谢致敬, 田中平, 李玥莹, 郑明心, 房帅, 米尔卡米力∙麦麦提, 依里帆∙艾克拜尔江, 高梅香, 张健. 微地形生境异质性对新疆西天山森林土壤跳虫群落分异的塑造作用[J]. 生物多样性, 2026, 34(4): 25300-. |
| [3] | 周铝, 姚世贸, 赵战合, 郭画, 田成. 庞泉沟国家级自然保护区狍和野猪时空共存格局[J]. 生物多样性, 2026, 34(2): 25327-. |
| [4] | 罗钰, 郑旭艳, 曹力, 王波, 彭艳琼, 罗银玲, 周会平, 杨小芳, 苗白鸽, 王朝雅, 高洁. 生境简化重塑榕树-榕小蜂互作网络: 挥发物组成与群落结构的适应性响应[J]. 生物多样性, 2026, 34(2): 25328-. |
| [5] | 黎明, 秦响玲, 朱玉茹, 熊文. 自然保护区生物多样性抵消价值实现的理论框架与运行机制[J]. 生物多样性, 2026, 34(1): 25241-. |
| [6] | 岳可欣, 牛钟辉, 刘念, 徐琳, 吕韦韦, 徐茂宏, 崔绍朋. 山西历山三种同域分布食肉动物昼夜活动节律及与月光周期的关系[J]. 生物多样性, 2025, 33(9): 25084-. |
| [7] | 田璐瑶, 尹豪. 基于生物多样性保护的我国生态铁路现状和对策研究[J]. 生物多样性, 2025, 33(8): 24495-. |
| [8] | 李玉, 周立志. 淮河干流越冬水鸟多样性的时空格局及其影响因素[J]. 生物多样性, 2025, 33(8): 24590-. |
| [9] | 徐进博, 崔雅倩, 王渊, 王伟波, 刘锋, 王广龙, 扈晶晶, 普布顿珠, 边巴多吉, 旦增, 胡开, 王小川, 宋刚, 吕永磊, 温知新. 西藏雅鲁藏布大峡谷国家级自然保护区内白颊猕猴的栖息地适宜性评价[J]. 生物多样性, 2025, 33(7): 24493-. |
| [10] | 田书荣, 魏营, 肖芬, 周芸芸, 解宜兴, 王丞, 宋芬, 梁志强, 桂小杰. 湖南张家界大鲵国家级自然保护区中国大鲵种群动态及保护策略[J]. 生物多样性, 2025, 33(7): 24581-. |
| [11] | 彭文, 邓泽帅, 郑文宝, 龚凌轩, 曾玉枫, 孟昊, 陈军, 杨道德. eDNA技术在两栖动物调查中的应用: 以湖南莽山国家级自然保护区为例[J]. 生物多样性, 2025, 33(6): 24552-. |
| [12] | 毛静, 王婧, 黄杰, 熊姝红, 张自亮, 张佑祥, 吴涛. 湖南高望界国家级自然保护区2021-2023年鸟兽多样性监测数据集[J]. 生物多样性, 2025, 33(6): 24489-. |
| [13] | 康燕, 干靓, 俞霖琳, 何晨静, 张理卿, 吴婧彬. 基于NbS的城市小微栖息地营造与网络构建模式: 以上海市长宁区生境花园为例[J]. 生物多样性, 2025, 33(5): 24528-. |
| [14] | 徐欢, 辛凤飞, 施宏亮, 袁琳, 薄顺奇, 赵欣怡, 邓帅涛, 潘婷婷, 余婧, 孙赛赛, 薛程. 生态修复技术集成应用对长江口北支生境与鸟类多样性提升效果评估[J]. 生物多样性, 2025, 33(5): 24478-. |
| [15] | 张晶晶, 黄文彬, 陈奕廷, 杨泽鹏, 柯伟业, 彭昭杰, 魏世超, 张志伟, 胡怡思, 余文华, 周文良. 广东南澎列岛海洋生态国家级自然保护区造礁石珊瑚多样性及分布特征[J]. 生物多样性, 2025, 33(4): 24424-. |
| 阅读次数 | ||||||
|
全文 |
|
|||||
|
摘要 |
|
|||||
备案号:京ICP备16067583号-7
Copyright © 2026 版权所有 《生物多样性》编辑部
地址: 北京香山南辛村20号, 邮编:100093
电话: 010-62836137, 62836665 E-mail: biodiversity@ibcas.ac.cn