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 |
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