Analysis of Space Utilization Characteristics of Human Activities and Giant Pandas(<i>Ailuropoda melanoleuca</i>) in Wolong Nature Reserve

DEME Luo-ying; WANG Xiao; ZHANG Jin-dong

doi:10.16779/j.cnki.1003-5508.2019.05.012

Volume 40 Issue 5

Nov. 2019

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DEME Luo-ying, WANG Xiao, ZHANG Jin-dong. Analysis of Space Utilization Characteristics of Human Activities and Giant Pandas(Ailuropoda melanoleuca) in Wolong Nature Reserve[J]. Journal of Sichuan Forestry Science and Technology, 2019, 40(5): 60-65. doi: 10.16779/j.cnki.1003-5508.2019.05.012

Citation:

DEME Luo-ying, WANG Xiao, ZHANG Jin-dong. Analysis of Space Utilization Characteristics of Human Activities and Giant Pandas(Ailuropoda melanoleuca) in Wolong Nature Reserve[J]. Journal of Sichuan Forestry Science and Technology, 2019, 40(5): 60-65. doi: 10.16779/j.cnki.1003-5508.2019.05.012

Analysis of Space Utilization Characteristics of Human Activities and Giant Pandas(Ailuropoda melanoleuca) in Wolong Nature Reserve

doi: 10.16779/j.cnki.1003-5508.2019.05.012

More Information

College of Life Sciences, China West Normal University, Nanchong 637000, China

Received Date: 2019-07-26

Abstract

There were three main hypotheses of spatial coexistence between wild animals and human beings, which were co-existence at regional scale, co-existence at intermediate scale and co-existence at fine scale. Identifying the space utilization mode of humans and wild animals could provide scientific reference for the protection and management of wild animals. Therefore, infrared cameras were used to monitor the activities of giant pandas (Ailuropoda melanoleuca) and human activities in the centralized distribution area of giant pandas in Wolong Nature Reserve. The coexistence mechanism between giant panda and humans was discussed by analyzing the spatial distribution characteristics of giant pandas and human activities. The results showed that (1) at the beginning of the study (2011.11-2013.04), the monthly relative abundance of human activities was relatively low, while the monthly relative abundance of giant pandas detected in this region was relatively high. However, since May 2013, the intensity of human activities increased sharply and stably at a high level, which resulted in a sharp decrease in the monthly relative abundance of giant pandas. (2) Although the use of key limiting factors (such as water sources) led to the overlaps of giant pandas and human activities, in general, the occurrence frequency of giant pandas significantly reduced in regions where human activities frequently occurred. Based on analysis of the three mechanisms of human and wildlife coexistence, the coexistence mode was co-existence at intermediate scale between giant pandas and human activities. Human activities restricted the survival and development of wild animals to a certain extent. The management department should fully consider the impact of human disturbance activities on giant pandas, formulate policies for sustainable development, meanwhile, reduce competition for space and resources between humans and giant pandas.
- Coexistence mechanism;
- Giant panda (Ailuropoda melanoleuca);
- Human activities;
- Infrared camera;
- Wolong Nature Reserve

References

[1]	郭海燕. 人类干扰对王朗自然保护区大熊猫及其栖息地的影响[D]. 四川大学,2003.
[2]	王化儒. 基于遥感的东北虎生境变化及其原因分析[D]. 北京师范大学,2012.
[3]	冰蓝.猴王喊你巡山去[J]. 中国周刊, 2016, (7 ).
[4]	张敏, 李凭, 邵义, 等. 自然保护区建设在野生动物保护中的作用[J]. 辽宁林业科技,2007,(3):51~52.
[5]	李缅. 新知识新信息[J]. 思想政治课教学,1993,(12 ).
[6]	Li B B, Pimm S L, Sheng L, et al. Free-ranging livestock threaten the long-term survival of giant pandas[J]. Biological Conservation,2017,216:18~25.
[7]	Carter N H, Shrestha B K, Karki J B, et al.Coexistence between wildlife and humans at fine spatial scales[J]. Proceedings of the National Academy of Sciences,2012,109(38):15360~15365.
[8]	周学红, 蒋琳, 王强, 等.朱鹮游荡期对人类干扰的耐受性[J]. 生态学报,2009,29(10).
[9]	史飞. 城市中松鼠觅食过程对人类活动产生的适应性行为[J]. 安徽农业科学,2015,(15):141~142.
[10]	冉江洪. 小相岭大熊猫种群生态学和保护策略研究[D]. 四川大学,2004.
[11]	四川省林业厅. 四川省第四次大熊猫调查报告[M].成都:四川科学技术出版社,2015.
[12]	唐小平, 贾建生, 王志臣, 等. 全国第四次大熊猫调查方案设计及主要结果分析[J]. 林业资源管理,2015, (1):11~16.
[13]	Hull V, Zhang J, Zhou S, et al. Impact of livestock on giant pandas and their habitat[J]. Journal for Nature Conservation,2014,22(3):256~264.
[14]	Wei F, Costanza R, Qiang D, et al. The Value of Ecosystem Services from Giant Panda Reserves[J]. Current Biology, 2018,28(13):2174~2180.
[15]	王学志. 岷山地区人类活动干扰对大熊猫生境利用的影响研究[D]. 中国科学院研究生院,2008.
[16]	白文科, 张晋东, 杨霞, 等. 基于GIS的卧龙自然保护区大熊猫生境选择与利用[J]. 生态环境学报, 2017,26(01):73~80.
[17]	周世强, Vanessa, HULL, 等. 野生大熊猫与放牧家畜的空间利用格局比较[J]. 兽类学报, 2016,36(2):138~151.
[18]	张晋东, 李玉杰, 李仁贵, 等. 红外相机技术在珍稀兽类活动模式研究中的应用[J]. 四川动物, 2015,34(5):671~676.
[19]	Huang J, Li Y Z, Du L M, et al. Genome-wide survey and analysis of microsatellites in giant panda (Ailuropoda melanoleuca), with a focus on the applications of a novel microsatellite marker system[J]. BMC Genomics, 2015,16(1):61.
[20]	王晓, 侯金, 张晋东, 等.同域分布的珍稀野生动物对放牧的行为响应策略[J]. 生态学报, 2018a, 38(18):129 ~137.
[21]	Liu X, Wu P, Songer M, et al. Monitoring wildlife abundance and diversity with infrared camera traps in Guanyinshan Nature Reserve of Shaanxi Province, China[J]. Ecological Indicators, 2013,33(Sp. Iss. SI):121~128.
[22]	武鹏飞, 刘雪华, 蔡琼, 等. 红外相机技术在陕西观音山自然保护区兽类监测研究中的应用[J]. 兽类学报,2012., 32(1):67 ~71.
[23]	张晋东. 人类与自然干扰下大熊猫空间利用与活动模式研究[D]. 中国科学院研究生院,2012.
[24]
[25]	王晓, 李玉杰, 李程, 等. 卧龙自然保护区放牧对大熊猫的影响[J]. 西华师范大学学报:自然科学版, 2018b,39(1):11~15.
[26]	Zhang J, T Connor, H Yang, et al. Complex effects of natural disasters on protected areas through altering telecouplings[J]. Ecology and Society,2018,23(3):17.
[27]	胡锦矗, 夏勒. 卧龙的大熊猫[M]. 成都:四川科学技术出版社,1985.
[28]	Zhang J, Hull V, Ouyang Z, et al. Divergent responses of sympatric species to livestock encroachment at fine spatiotemporal scales[J]. Biological Conservation, 2017,209:119~129.
[29]	姜广顺. 多空间尺度下驼鹿和狍受人类干扰的生态效应及其适应机制研究[D]. 东北林业大学,2007.
[30]	葛晨. 人类干扰下的野生鸟类警戒行为研究[D]. 南京大学,2012.
[31]	刘亚儒, 杨绣坤. 我国野生动植物资源利用的现状与保护[J]. 现代园艺, 2018,366(18):159.

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通讯作者: 陈斌, bchen63@163.com

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沈阳化工大学材料科学与工程学院沈阳 110142

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Analysis of Space Utilization Characteristics of Human Activities and Giant Pandas(Ailuropoda melanoleuca) in Wolong Nature Reserve

College of Life Sciences, China West Normal University, Nanchong 637000, China

Received Date: 2019-07-26

Key words:

Coexistence mechanism /
Giant panda (Ailuropoda melanoleuca) /
Human activities /
Infrared camera /
Wolong Nature Reserve

Abstract: There were three main hypotheses of spatial coexistence between wild animals and human beings, which were co-existence at regional scale, co-existence at intermediate scale and co-existence at fine scale. Identifying the space utilization mode of humans and wild animals could provide scientific reference for the protection and management of wild animals. Therefore, infrared cameras were used to monitor the activities of giant pandas (Ailuropoda melanoleuca) and human activities in the centralized distribution area of giant pandas in Wolong Nature Reserve. The coexistence mechanism between giant panda and humans was discussed by analyzing the spatial distribution characteristics of giant pandas and human activities. The results showed that (1) at the beginning of the study (2011.11-2013.04), the monthly relative abundance of human activities was relatively low, while the monthly relative abundance of giant pandas detected in this region was relatively high. However, since May 2013, the intensity of human activities increased sharply and stably at a high level, which resulted in a sharp decrease in the monthly relative abundance of giant pandas. (2) Although the use of key limiting factors (such as water sources) led to the overlaps of giant pandas and human activities, in general, the occurrence frequency of giant pandas significantly reduced in regions where human activities frequently occurred. Based on analysis of the three mechanisms of human and wildlife coexistence, the coexistence mode was co-existence at intermediate scale between giant pandas and human activities. Human activities restricted the survival and development of wild animals to a certain extent. The management department should fully consider the impact of human disturbance activities on giant pandas, formulate policies for sustainable development, meanwhile, reduce competition for space and resources between humans and giant pandas.

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Reference (31)

[1]	郭海燕. 人类干扰对王朗自然保护区大熊猫及其栖息地的影响[D]. 四川大学,2003.
[2]	王化儒. 基于遥感的东北虎生境变化及其原因分析[D]. 北京师范大学,2012.
[3]	冰蓝.猴王喊你巡山去[J]. 中国周刊, 2016, (7	).
[4]	张敏, 李凭, 邵义, 等. 自然保护区建设在野生动物保护中的作用[J]. 辽宁林业科技,2007,(3):51~52.
[5]	李缅. 新知识新信息[J]. 思想政治课教学,1993,(12	).
[6]	Li B B, Pimm S L, Sheng L, et al. Free-ranging livestock threaten the long-term survival of giant pandas[J]. Biological Conservation,2017,216:18~25.
[7]	Carter N H, Shrestha B K, Karki J B, et al.Coexistence between wildlife and humans at fine spatial scales[J]. Proceedings of the National Academy of Sciences,2012,109(38):15360~15365.
[8]	周学红, 蒋琳, 王强, 等.朱鹮游荡期对人类干扰的耐受性[J]. 生态学报,2009,29(10).
[9]	史飞. 城市中松鼠觅食过程对人类活动产生的适应性行为[J]. 安徽农业科学,2015,(15):141~142.
[10]	冉江洪. 小相岭大熊猫种群生态学和保护策略研究[D]. 四川大学,2004.
[11]	四川省林业厅. 四川省第四次大熊猫调查报告[M].成都:四川科学技术出版社,2015.
[12]	唐小平, 贾建生, 王志臣, 等. 全国第四次大熊猫调查方案设计及主要结果分析[J]. 林业资源管理,2015, (1):11~16.
[13]	Hull V, Zhang J, Zhou S, et al. Impact of livestock on giant pandas and their habitat[J]. Journal for Nature Conservation,2014,22(3):256~264.
[14]	Wei F, Costanza R, Qiang D, et al. The Value of Ecosystem Services from Giant Panda Reserves[J]. Current Biology, 2018,28(13):2174~2180.
[15]	王学志. 岷山地区人类活动干扰对大熊猫生境利用的影响研究[D]. 中国科学院研究生院,2008.
[16]	白文科, 张晋东, 杨霞, 等. 基于GIS的卧龙自然保护区大熊猫生境选择与利用[J]. 生态环境学报, 2017,26(01):73~80.
[17]	周世强, Vanessa, HULL, 等. 野生大熊猫与放牧家畜的空间利用格局比较[J]. 兽类学报, 2016,36(2):138~151.
[18]	张晋东, 李玉杰, 李仁贵, 等. 红外相机技术在珍稀兽类活动模式研究中的应用[J]. 四川动物, 2015,34(5):671~676.
[19]	Huang J, Li Y Z, Du L M, et al. Genome-wide survey and analysis of microsatellites in giant panda (Ailuropoda melanoleuca), with a focus on the applications of a novel microsatellite marker system[J]. BMC Genomics, 2015,16(1):61.
[20]	王晓, 侯金, 张晋东, 等.同域分布的珍稀野生动物对放牧的行为响应策略[J]. 生态学报, 2018a, 38(18):129	~137.
[21]	Liu X, Wu P, Songer M, et al. Monitoring wildlife abundance and diversity with infrared camera traps in Guanyinshan Nature Reserve of Shaanxi Province, China[J]. Ecological Indicators, 2013,33(Sp. Iss. SI):121~128.
[22]	武鹏飞, 刘雪华, 蔡琼, 等. 红外相机技术在陕西观音山自然保护区兽类监测研究中的应用[J]. 兽类学报,2012., 32(1):67	~71.
[23]	张晋东. 人类与自然干扰下大熊猫空间利用与活动模式研究[D]. 中国科学院研究生院,2012.
[24]
[25]	王晓, 李玉杰, 李程, 等. 卧龙自然保护区放牧对大熊猫的影响[J]. 西华师范大学学报:自然科学版, 2018b,39(1):11~15.
[26]	Zhang J, T Connor, H Yang, et al. Complex effects of natural disasters on protected areas through altering telecouplings[J]. Ecology and Society,2018,23(3):17.
[27]	胡锦矗, 夏勒. 卧龙的大熊猫[M]. 成都:四川科学技术出版社,1985.
[28]	Zhang J, Hull V, Ouyang Z, et al. Divergent responses of sympatric species to livestock encroachment at fine spatiotemporal scales[J]. Biological Conservation, 2017,209:119~129.
[29]	姜广顺. 多空间尺度下驼鹿和狍受人类干扰的生态效应及其适应机制研究[D]. 东北林业大学,2007.
[30]	葛晨. 人类干扰下的野生鸟类警戒行为研究[D]. 南京大学,2012.
[31]	刘亚儒, 杨绣坤. 我国野生动植物资源利用的现状与保护[J]. 现代园艺, 2018,366(18):159.

Analysis of Space Utilization Characteristics of Human Activities and Giant Pandas(Ailuropoda melanoleuca) in Wolong Nature Reserve

doi: 10.16779/j.cnki.1003-5508.2019.05.012

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Analysis of Space Utilization Characteristics of Human Activities and Giant Pandas(Ailuropoda melanoleuca) in Wolong Nature Reserve

doi: 10.16779/j.cnki.1003-5508.2019.05.012

College of Life Sciences, China West Normal University, Nanchong 637000, China

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Analysis of Space Utilization Characteristics of Human Activities and Giant Pandas(Ailuropoda melanoleuca) in Wolong Nature Reserve

doi: 10.16779/j.cnki.1003-5508.2019.05.012

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通讯作者: 陈斌, bchen63@163.com

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Analysis of Space Utilization Characteristics of Human Activities and Giant Pandas(Ailuropoda melanoleuca) in Wolong Nature Reserve

doi: 10.16779/j.cnki.1003-5508.2019.05.012

College of Life Sciences, China West Normal University, Nanchong 637000, China

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