红外相机最小监测强度的影响因素研究

大理大学学报

红外相机最小监测强度的影响因素研究

（1.大理大学东喜玛拉雅研究院，云南大理 671003；2.兰坪云岭省级自然保护区管护局，
云南兰坪 671400）

收稿日期:2019-07-03 出版日期:2020-06-15 发布日期:2020-06-15
作者简介:张永俊，2016级生物科学专业本科生。
基金资助:
国家自然科学基金项目（31860164；31860168；31760126；31560118）；大理大学博士启动费项目（KYBS201509）

Study on the Influencing Factors of the Minimum Trapping Effort of Infrared Camera

（1. Institute of Eastern-Himalaya Biodiversity Research, Dali, Yunnan 671003, China; 2. Management and Protection Bureau of
Yunling Provincial Nature Reserves in Lanping County, Nujiang, Yunnan 671400, China）

Received:2019-07-03 Online:2020-06-15 Published:2020-06-15
Supported by:

摘要/Abstract

摘要： 目的：了解植被类型、海拔和季节对红外相机所需最小监测强度（minimum trapping effort,MTE），即监测时长的影响。方法：在兰坪云岭省级自然保护区位于海拔 3 400 m的灌丛、常/落阔混交林、针叶林和针阔混交林，以及海拔分别为3 100、3 400、3 700 m 的常/落阔混交林开展红外相机监测。结果：为期 1 年的监测，累积有效拍摄 3 785 d，获得独立照片（independent photograph，IP）508张。各植被类型和海拔中，仅有灌丛和最高海拔（3 700 m）的红外相机达到MTE。各植被类型（Sørenson Index：S Max =47.62%，S Min =25.00%）和海拔（Sørenson Index：S Max =50.00%，S Min =17.65%）的物种多样性相似度均较低。所有相机位点：雨季监测的物种数、IP值及其累积速率均高于旱季，且雨/旱季的物种多样性的相似度仅为43.14%。结论：在物种多样性监测研究中，可在灌丛和高海拔位点合理减少监测时长，但总体而言，监测期不应少于1年，且需包含雨季和旱季，同时，相机位点应该覆盖更多的植被类型，加大海拔分辨率。

关键词: 红外相机, MTE, 植被类型, 海拔, 季节

Abstract: Objective: To understand the effects of vegetation type, elevation and season on the minimum trapping effort（MTE）required for infrared camera, i.e. the duration of the monitoring. Methods: This camera trap study was located in the Lanping Yunling Provincial Nature Reserves at the elevation of 3 400 m and the vegetation types of shrubs, constant/lost mixed forest, the coniferous forests and coniferous and broad-leaved mixed forest, and the vegetation type of constant/lost mixed forest and the elevation of 3 100,3 400, 3 700 m respectively. Results: During the 1-year monitoring period, the cumulative effective shooting was 3 785 d, and 508

independentphotograph（IP）wereobtained.Amongthevegetation typesand elevations,onlytheshrub an the highestelevation（3 700 m）

camera trap reached the MTE. The species diversity of the vegetation types（Sørenson Index: S Max = 47.62%, S Min = 25.00%）and altitude

（Sørenson Index: S Max = 50.00%, S Min = 17.65%）were lower. All camera sites: The number of species, IP account and accumulation rate

during the rainy season were higher than the dry season, and the similarity of species diversity in the rain/dry season was only 43.14%.

Conclusion: In the species diversity monitoring study, the monitoring duration can be reasonably reduced at the shrub and high-

altitude sites, but in general, the monitoring period should be no less than 1 year, and the rainy and dry seasons should be included.

More vegetation types should be covered and altitude resolution should be increased.

Key words: infrared camera, MTE, vegetation types, elevation, season

中图分类号:

张永俊，和育超，谭坤，房以好，陈尧，肖文，黄志旁. 红外相机最小监测强度的影响因素研究[J]. 大理大学学报.

Zhang Yongjun,He Yuchao, Tan Kun, Fang Yihao,Chen Yao, Xiao Wen, Huang Zhipang. Study on the Influencing Factors of the Minimum Trapping Effort of Infrared Camera[J]. Journal of Dali University.

参考文献

〔1〕LI S，MCSHEA W J，WANG D J，et al. The Use of Infrared-

Triggered Cameras for Surveying Phasianids in Sichuan

Province，China〔J〕. IBIS，2010，152（2）：299-309.

〔2〕AHUMADA J A，SILVA C E F，GAJAPERSAD K，et al.

Community Structure and Diversity of Tropical Forest

Mammals：Data from a Global Camera Trap Network〔J〕.

Philosophical Transactions of the Royal Society B（Bio?

logical Sciences），2011，366（1578）：2703-2711.

〔3〕SILVER S C，OSTRO L E T，MARSH L K，et al. The Use of

Camera Traps for Estimating Jaguar Panthera onca Abun?

dance and Density Using Capture/Recapture Analysis〔J〕.

Oryx，2004，38（2）：148-154.

〔4〕WECKEL M，GIULIANO W，SILVER S. Jaguar（Panthera

onca）Feeding Ecology：Distribution of Predator and Prey

Through Time and Space〔J〕. Journal of Zoology，2006，270

（1）：25-30.

〔5〕OLIVEIRA-SANTOS L G R，TORTATO M A，GRAIPEL M

E. Activity Pattern of Atlantic Forest Small Arboreal

Mammals as Revealed by Camera Traps〔J〕. Journal of

Tropical Ecology，2008，24（5）：563-567.

〔6〕WEGGE P，POKHERAL C P，JNAWALI S R. Effects of

Trapping Effort and Trap Shyness on Estimates of Tiger

Abundance from Camera Trap Studies〔J〕. Animal Conser?

vation，2004，7（3）：251-256.

〔7〕YASUDA M. Monitoring Diversity and Abundance of Mam?

mals with Camera Traps：A Case Study on Mount Tsukuba，

Central Japan〔J〕. Mammal Study，2004，29（1）：37-46.

〔8〕TROLLE M，KÉRY M. Camera-Trap Study of Ocelot and

Other Secretive Mammals in the Northern Pantanal〔J〕.

Mammalia，2005，69（3/4）：405-412.

〔9〕BAZZAZ F A. Plant Species Diversity in Old-Field Suc?

cessional Ecosystems in Southern Illinois 〔J〕. Ecology，1975，

56（2）：485-488.

〔10〕LAWTON J H. Plant Architecture and the Diversity of

Phytophagous Insects〔J〕. Annual Review of Entomology，

1983，28（1）：23-39.

〔11〕PALMER M W. Variation in Species Richness：Towards

a Unification of Hypotheses〔J〕. Folia Geobotanica et Phy?

totaxonomica，1994，29（4）：511-530.

〔12〕ROVERO F，MARSHALL A R. Camera Trapping Photo?

graphic Rate as an Index of Density in Forest Ungulates〔J〕.

Journal of Applied Ecology，2009，46（5）：1011-1017.

〔13〕HUANG Z P，CUI L W，SCOTT M B，et al. Seasonality

of Reproduction of Wild Black-and-White Snub-Nosed

Monkeys（Rhinopithecus bieti）at Mt. Lasha，Yunnan，China

〔J〕. Primates，2012，53（3）：237-245.

〔14〕HUANG Z P，SCOTT M B，LI Y P，et al. Black-and-White

Snub-Nosed Monkey（Rhinopithecus bieti）Feeding Behav?

ior in a Degraded Forest Fragment：Clues to a Stressed

Population〔J〕. Primates，2017，58：517-524.

〔15〕STEIN A B，FULLER T K，MARKER L L. Opportunistic

Use of Camera Traps to Assess Habitat-Specific Mammal

and Bird Diversity in Northcentral Namibia〔J〕. Biodiver?

sity and Conservation，2008，17（14）：3579-3587.

〔16〕BERNARD H，BAKING E L，GIORDANO A J，et al.

Terrestrial Mammal Species Richness and Composition in

Three Small Forest Patches within an Oil Palm Landscape

in Sabah，Malaysian Borneo〔J〕. Mammal Study，2014，39

（3）：141-154.

〔17〕FEI X H，SONG Q H，ZHANG Y P，et al. Patterns and

Controls of Light Use Efficiency in Four Contrasting Forest

Ecosystems in Yunnan，Southwest China〔J〕. Journal of

Geophysical Research：Biogeosciences，2019，124（2）：

293-311.

〔18〕房以好，任国鹏，高颖，等. 红外相机安放于地面和林

冠层对野生动物监测结果的影响〔J〕. 生物多样性，

2018，26（7）：717-726.

〔19〕SALINAS-RAMOS V B，HERRERA M L G，Morales-

Malacara J B. Seasons Influence Acarine Infestation in

Bats from Tropical Dry Forests of Western Mexico〔J〕.

MammalianBiology，2019，96：37-44.

〔20〕KARR J R. Seasonality，Resource Availability，and Com?

munity Diversity in Tropical Bird Communities〔J〕. The

American Naturalist，1976，110（976）：973-994.

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