Impacts of man-made provisioned food on learned cub behaviours of giant pandas in pre-release reintroduction training.
Key words: reintroduction, pre-release training, feces abundance, habitat selection, home range
Reintroduction has been seen as a valuable tool for conserving many threatened species (Short et al. 1992, Kleiman 1996). Many biological and ecological factors have been shown to contribute to the success or failure of a reintroduction project, such as the provenance of released animals (wild-caught or captive-born), type of release (soft or hard), and habitat (including food) suitability (Jule et al. 2008). In particular, there are many behavioural problems unique to captive-born carnivores, which include loss of socially learned skills (e.g. hunting and mating) and high levels of stereotypies or abnormal behaviours (Soorae & Stanley Price 1997). For instance, stereotypic behaviour has been reported in captive giant pandas (Liu et al. 2005). One method to enhance a captive-born individual's ability to adapt to wild environments is pre-release training and acclimatization (Beck et al. 1994, Kleiman 1996). Soft-releases allow for acclimation to a new location prior to release and allows animals time to gain familiarity with places to shelter and escape predation (Biggins et al. 1999). Pre-release training can assist reintroduced individuals in the development of anti-predator behaviour prior to reintroductions (Alberts 2007).
The giant panda (Ailuropoda melanoleuca) is a threatened species (IUCN 2016), and extensive efforts have been made by conservation biologists and wildlife managers to enlarge its populations. Limited by breeding ability and habitat fragmentation, the population size of wild giant pandas has oscillated from the 1980s to 2014 (State Forestry Administration 2015). On the other hand, the population of captive giant pandas has increased steadily since 2000, and reached 471 by the end of 2016 (Chinese Association of Zoological Gardens 2016). With the increasing captive population, managers are now able to reintroduce some of the captive giant pandas to their historical distribution area to recover local giant panda populations, or rejuvenate isolated small populations (Zhang et al. 2006, Lei et al. 2015).
The giant panda has been a top priority for conservation action in China since the 1950s (Hu et al. 1985), but the small habitat area and low population density of giant pandas in the Xiaoxiangling mountain region are challenging conservation efforts (State Forestry Administration 2015). Although faced with difficulties typical of captive-born animals released to the wild, the captive-born giant panda Xiangxiang was first released into Wolong Nature Reserve, China in April, 2006. To enlarge the small population and enrich the genetic diversity of the isolated Xiaoxiangling population, the next attempts at reintroduction were there. The captive-born giant pandas, Taotao and Zhangxiang, were pre-release trained in Wolong Nature Reserve, China in 2012 and 2013, respectively, and subsequently released in Liziping Nature Reserve of the Xiaoxiangling mountains, China.
Although giant pandas have historically specialized as a bamboo feeder with more than 99% of their annual diet consisting bamboo in the wild (Hu et al. 1985), previous studies have found that the diet of wild populations varies among different mountain regions (Hu et al. 1985, Pan et al. 2001, Hull et al. 2014). Spatial behaviour of giant pandas, especially for habitat selection, have also been shown to be very flexible (Hu et al. 1985, Pan et al. 2001, Hull et al. 2014, Hong et al. 2015, 2016). Flexibility in those behaviours can help giant pandas adapt to available environmental conditions (Hu et al. 1985, Zhang et al. 2009, Hull et al. 2014). Placed in enclosures for pre-release training and acclimatization, captive giant pandas experience environmental conditions that simulate the wild. Giant pandas may exhibit different behaviours, such as habitat selection, space use, and distances moved in pre-release training enclosures due to different levels of human disturbance, such as man-made food.
During the pre-release training and acclimatization phases of soft release, the effects of human disturbances on a captive born individual and its mother remain poorly understood. In this study, we monitored two pairs of mother-cub giant pandas in Hetaoping, Wolong National Nature Reserve, China. One mother giant panda was fed man-made food and the other pair was not, and we investigated the two pairs' spatial behaviours under the presence or absence of man-made food conditions. To do this, we: 1) surveyed and compared differences between the giant pandas' learning ability about habitat selections, 2) studied the variation of feces abundance among different habitat types, and 3) tested whether different individuals exhibited different home range patterns.
Material and Methods
The pre-release training enclosure used in this study covers about 24 [ha.sup.2] and is located at Hetaoping, in the northeast of Wolong National Nature Reserve (Fig. 1). The elevation range is from 2100 to 2400 m. The climate is dominated by the south-east monsoon from May to October, and continental air masses in the winter. The average annual rainfall is 1800 mm (winter snowfall averages 936 mm), with an average evaporation of 874 mm. The highest temperatures occur in July with daily average temperatures of 17 [degrees]C and the lowest occur in January with daily average temperatures of -1.7 [degrees]C. The study area features broad-leaved deciduous forest with dominant species of Juglan scathayensis, Rhus punjabensis var. sinica, Acer flabellatum. Both Fargesia robusta and Yushania brevipaniculata bamboo species exist in the pre-release training enclosure, with the former covering 95% of the study area.
[FIGURE 1 OMITTED]
To help the pre-released giant panda learn skills from its mother, we used mother with cub training methods. The male cub "Taotao" (designated CN for "cub with natural food") was born in Hetaoping on 3rd August 2010, and its mother "Caocao" (designated MN for "mother with natural food") was rescued from Qionglai mountain. Managers supplemented the other mother giant panda, "Zhangka", with provisioned man-made food (e.g. bamboo shoots and vitamin enriched biscuit) thrown onto grassy areas in the enclosure. The female cub "Zhangxiang" (designated CMF for "cub with man-made food") was born in Hetaoping on 20th August 2011, and its mother "Zhangka" (designated MMF for "mother with man-made food") was born in 2000 and rescued from Qionglai mountain. MN-CN were first transferred into the acclimatization enclosure for pre-release training on 3rd May 2012. After CN was released into wild on 11th October 2012, MMF-CMF were transferred into the same acclimatization enclosure on 21st November 2012 for pre-release training. CMF was transported into another acclimatization enclosure for further pre-release training in the Liziping Nature Reserve on 6th November 2013. Detailed information for all giant pandas can be found in Table 1.
Field surveys were conducted on the entire enclosure from 11th October to 23rd October 2012, and 6th November to 29th November 2013 after pre-release training. We set transect lines at roughly 100 m equidistant from each other following the methods of Wei et al. (2000), Zhang et al. (2006) and Hong et al. (2015). Along transect lines, we established microhabitat plots (20 x 20 [m.sup.2]) centered on fecal deposits and feeding sign encountered, with the distance from each other not less than 60 m gain in elevation or not less than 100 m in horizontal distance. All microhabitat plots were set and sampled following the methods of Wei et al. (2000) and Zhang et al. (2006). Sixteen variables reflecting slope, trees, shrubs, and bamboo were measured (Table 2). During field surveys, we recorded the total number of individual feces droppings and dropping groups, respectively, following Hong et al. (2015). We recorded the GPS coordinates of each fecal deposit and feeding sign of both the cub and the mother, and mapped the presence of bamboo edge, bamboo interior, bushwood, and grassland in the understory. We could easily distinguish the feces of the mother from the cub because the cub's feces were much smaller (means [+ or -] standard deviation length: 7.71 [+ or -] 0.69, width: 2.76 [+ or -] 0.30 cm) than those of the mother's (13.28 [+ or -] 0.85 and 5.20 [+ or -] 0.63 cm). To avoid repeated sampling, all microhabitat plots were surveyed only once during the study period, and panda feces in microhabitat plots were destroyed after the survey.
We first used one-sample Kolmogorov-Smirnov test to check if the data were normally distributed, and then conducted independent sample t-tests to compare variables between cub and mother microhabitat plots when data were normally distributed or Mann-Whitney U test when the distributional assumptions were not met. Only variables with significant difference were involved in subsequent analyses. For those predictor variables with a correlation coefficient above 0.60, the variable with a clearer biological meaning was retained for further analysis to weaken collinearity (Liang & Thomson 1994, Fabrizio et al. 2003, Sebastien et al. 2003). Correlation coefficients were calculated through Pearson correlation analysis when data were normally distributed or Spearman correlation analysis when data were not normally distributed. Stepwise discriminant function analysis was adopted to assess the relative importance of variables contributing to the difference of microhabitat plots between the cub and mother giant panda.
To uncover the effects of provisioning man-made food on cub's learned microhabitat selection, we first calculated ratios of variables (variables in microhabitat plots of cub divided by those of its mother) and then compared them between the two pre-release feeding conditions (provisioned food versus natural foraging conditions) through independent samples t-tests (normally distributed) or Mann-Whitney U test (not normally distributed). Stepwise discriminant function analysis was used to assess the importance of variables in contributing to differences in microhabitat selection between the two feeding conditions.
To compare the spatial behaviour of giant pandas, we tracked each panda using high-resolution global positioning system (GPS) telemetry. We then calculated minimum convex polygon home ranges using the Geospatial Modelling Environment program (Beyer 2011). The relative proportion of each giant panda's feces number range from different habitat types were compared through chi-square test, a method that was also used to compare the home range size among each giant panda. We also conducted independent samples t-tests to compare the number of feces per site between giant pandas (when data were normally distributed) or Mann-Whitney U test (data not normally distributed). All statistical tests were two-tailed and conducted in SPSS 17.0 (SPSS Inc.. Chicago, U.S.A.). Data are presented as mean [+ or -] SD, and the significance level of all analyses was 0.05.
[FIGURE 2 OMITTED]
[FIGURE 3 OMITTED]
[FIGURE 4 OMITTED]
Differences in microhabitat selected by captive-born giant panda cubs and their mothers
There was no significant difference between variables selected by MN-CN pair through independent samples t-test or Mann-Whitney U test (Table 3). Microhabitat plots selected by CMF differed significantly from those selected by MMF in 14 variables (all except shrub dispersion and shrub DBH, Table 3), indicating MMF-CMF pair exhibited different microhabitat selection patterns. Only five variables (canopy, shrub size, shelter distance, tree dispersion and water distance) were entered into the last discriminant function. These variables made greater contributions to differentiating the microhabitat plots of CMF from those of MMF (f = 52.70, df=5, p< 0.001; Table 4), with an overall correct prediction rate of 88.46% (Table 5). Compared to MMF, CMF tended to select microhabitat that had higher overstory canopy, lower understory coverage, was closer to shelter, and was farther from water sources.
Difference in cub microhabitat selection learned from its mother between pairs exposed to natural vs. provisioned man-made food
Ratios of all microhabitat variables between mother and cub differed significantly in the man-made food pair, indicating the giant panda cubs exhibited different microhabitat selection patterns learned from its mother under the presence of man-made food (Table 3). Only canopy, shrub dispersion, distance from water, and grass coverage entered the last discriminant function and made greater contribution to differentiating microhabitat selection between the two types of food resources ([[CHI].sup.2] = 88.80, df = 4, p < 0.001; Table 4), with an overall correct prediction rate of 95.16%(Table 5).
Compared to MMF, CMF significantly selected higher overstory canopy (p < 0.001), farther water resources (p < 0.001) and lower grass coverage (p < 0.001), but no significant difference was found in those variables between CN and MN (Table 3). Difference between ratios of shrub dispersion reflected that CMF selected areas with more shrubs compared to MMF, than CN did compared to its mother MN (Table 3).
Comparison of fecal deposition of each giant panda in different habitats
CMF was the only giant panda in this study that deposited feces in bushwood. Excluding this habitat, the relative proportion of the number of feces in the other three habitats were significantly different among the four giant pandas for bamboo edge ([[CHI].sup.2] = 24.95, df = 3,p < 0.001), for bamboo interior ([[CHI].sup.2] = 46.39, df = 3,p < 0.001), and for grass land ([[CHI].sup.2] = 107.68, df = 3, p < 0.001; Fig. 2). No significant difference existed in relative proportion of feces in the three habitat types between MN and CN. The relative number of feces of MMF in bamboo edge and interior were significantly less than that of CMF ([[CHI].sup.2] = 5.43, df = 1, p = 0.02; and [[CHI].sup.2] = 22.15, df = 1, p < 0.001; respectively), and there were relatively more feces in grass land than that of CMF ([[CHI].sup.2] = 35.84, df = 1, p < 0.001). MN more frequently appeared in bamboo edge ([[CHI].sup.2] = 19.56, df = 1, p < 0.001) with lower frequency in grass land ([[CHI].sup.2] = 42.25, df = 1, p< 0.001) than MMF. CN also more frequently appeared in bamboo edge habitat ([[CHI].sup.2] = 4.64, df = 1, p = 0.03), but had a lower frequency in bamboo interior ([[CHI].sup.2] = 13.33, df = 1, p < 0.001) than CMF.
Comparison of home range and trace abundance of different giant pandas
The home range among the four giant pandas was significantly different (Fig. 3; [[CHI].sup.2] = 23.41, df = 3, p < 0.001). There was no difference in home range between MN and CN or MMF and CMF (Fig. 3). However, the home range of MN was larger than MMF ([[CHI].sup.2] = 17.86, df = 1, p < 0.001), and the home range of CN was larger than CMF ([[CHI].sup.2] = 5.43, df = 1, p = 0.02). The average number of feces among the four giant pandas was significantly different (Fig. 4; F = 8.27, df = 3, p < 0.001). Even though no significant difference of average feces number existed between MN and MMF or CN and CMF, the average number of feces of the cubs in each pair was a little less than that of the mothers (Fig. 4).
Mammals not only provide sustenance and protection to their offspring, but also teach them a variety of life skills during the rearing phase (Sun 2001). Our results clearly indicate that mother-cub pairs raised in pre-release training enclosures relying on entirely natural forage (MN-CN) exhibited similar microhabitat selection patterns, which parallels reports by Zhang et al. (2013). Provisioning man-made food to MMF-CMF resulted in different microhabitat selection between the pair in almost all habitat variables. In particular, in contrast to its mother, CMF preferred higher canopy and areas closer to shelter. Living in solitude, giant pandas naturally avoid humans (Hu et al. 1985). Our results indicate that provisioning food to mother giant pandas caused the cub to select higher security habitat may have been caused by the presence of the humans providing food. Our results must be interpreted with caution as we only compared two cubs and this is the first study to compare microhabitat selection within the same enclosure. Almost all previous studies on habitat utilization surveyed all giant pandas in a given area (Hull et al. 2014). Future studies should focus on investigating the similarities or differences in habitat selection behaviours between sub-adult pandas and adult individuals when they coexist in one area.
Compared to the natural feeding regime, provisioning man-made food significantly impacted giant panda cub's learned microhabitat selection behaviours, especially in regards to overstory tree coverage, water resources, and grass coverage. Giant pandas retains a short carnivorous alimentary tract even though its diet is composed almost exclusively of bamboo (Hu et al. 1985). Thus, giant pandas have very low digestive efficiency and exhibit exceptionally low daily energy expenditure during extensive foraging sessions on bamboo foods (Nie et al. 2015). Habitats of higher canopy overstory possess more nutritious bamboo (Hu et al. 1985, Hong et al. 2016), but MMF received supplemental man-made food during pre-release training that provided additional energy supplements which probably made it unnecessary for her to seek out higher quality bamboo habitat featuring more overstory trees. This behaviour was markedly different from MN, who may have needed to spend more time seeking higher quality bamboo under high canopy under the all natural feeding regime, a behavioural preference that was also passed to her cub, CN (Table 2).
Without human provisioning of food, CN and its mother MN preferred bamboo edge habitats for higher quality foods (Yu et al. 2003), and exhibited similar habitat preference (Fig. 2). In contrast, CMF spent larger periods of time in bamboo interior for shelter and bamboo resources than its mother, CN, and the mother under the natural feeding regime, MN (Fig. 2).
This result may be explained by the interference caused by provisioning man-made food by the staff in grass land areas resulting in MMF spending more time on grass land consuming man-made food, subsequently spending less time teaching CMF to forage higher quality bamboo at bamboo edge habitats. In some bird species, offspring that receive low levels of care are less successful and have lower fitness (Kilner et al. 2015). We propose that CMF had less time learning skills from its mother and, therefore, CMF was found more in microhabitats with less bamboo and higher densities of vine and liana. It appears that the difference in behaviour between CMF and CN may be due to provisioning man-made food to MMF possibly resulting in less habitat selection mother-cub teaching opportunities for CMF. That provisioning mother pandas with man-made food significantly impacted cub giant panda habitat selection and foraging behaviours in the pre-release training program.
Commonly, an animal's home range may be defined as the area used to forage, mate, and foster offspring (Burt 1943). It is important to understand the spatial extent of an animal's home range, especially in comprehending a species' ecological development and in conserving adequate habitat for its survival (Connor et al. 2016). Multiple studies have found giant pandas have larger home ranges than previously thought when including data from periods longer than one year (Schaller et al. 1985, Yong et al. 2004, Hull et al. 2015). During the current study conducted over one month, home ranges of MN or MMF were obviously smaller than those of wild pandas in the Qionglai mountains (< 5.14 k[m.sup.2] [+ or -] 1.04, Hu et al. 1985). The home range of MMF was significantly smaller than both MN and CN's (Fig. 3). This indicates that provisioning man-made food significantly impacted MMF's movements, which subsequently impacted the size of CMF's home range. This result was also confirmed by the average number of feces of each panda, with higher average number of feces of MMF in areas provisioned with man-made food (Fig. 4).
In summary, our results indicate provisioning giant pandas with man-made food affected giant panda cub behaviours in the pre-release training program. Provisioning man-made food not only affected the mother giant panda's behaviours (i.e. MMF) but also may have hindered behavioural development of giant panda cubs during the acclimatization period, such as microhabitat selection and home range behaviours. We suggest that during pre-released training, anthropogenic interferences should be lessened and captive-born animals should be raised in the most natural conditions possible in order to develop appropriate behavioural repertoires.
A successful reintroduction program can be impacted by many factors, such as movement capacity, sufficient protected areas, diseases, community support, etc. (Kleiman et al. 1994, Zhang et al. 2006). Keeping other conditions normal, our results clearly demonstrate that man-made foods can affect the amount of time pre-released giant panda cubs learn from its mother within the training enclosure. This subsequently affected learned behaviours, most importantly habitat selection and movements. The cub whose mother was exposed to man-made food tended to use higher security areas and lower quality bamboo habitats, and had a smaller home range. Trying to match the pre-released training environments more closely to wild habitat and minimizing anthropogenic interference may increase the chances of captive-born released success (Stamps & Swaisgood 2007). Our study results lend credence to this theory and suggests that future pre-release training must lessen human interference as much as possible during the whole acclimatization period.
The "Captive Giant Panda Release Project" was launched approximately 10 years ago, and CN and CMF were released into Liziping Nature Reserve. Perhaps resulting from its mother's exposure to man-made foods in the pre-release, CMF exhibited different microhabitat selection and foraging strategies from wild giant pandas in Liziping Nature Reserve (Lei et al. 2015). Because anthropogenic interference may significantly influence sub-adult pandas, which may persist into adulthood (Nussey et al. 2007), we suggest that future pre-released training of captive individuals should be conducted under natural conditions in order to increase the likelihood of survivorship in the wild. Though our study was conducted on giant pandas, our results may have far reaching implications for other captive-bred animals slated for reintroduction. Anthropogenic interference may significantly influence behavioural development, which could potentially adversely affect reintroduction survivorship. Pre-release training programs that prepare captive-born vertebrates for reintroduction should fully consider the potential impacts of even limited anthropogenic interference.
This research was funded by the Wolong Club Foundation (WPC-20 (15-18) -03) and the Giant Panda International Cooperation Research Project (SD1115). Thanks to Thomas Connor, Meghan Martin and Dr. Jingdong Zhang for their comments and English modifications of the manuscript. Thanks to Wenbin Yang and Hong Yang for assistance collecting data in the field.
Alberts A.C. 2007: Behavioral considerations of head starting as a conservation strategy for endangered Caribbean rock iguanas. Appl. Anim. Behav. Sci. 102: 380-391.
Beck B.B., Rapaport L.G., Stanley Price M.R. & Wilson A.C. 1994: Reintroduction of captive-born animals. In: Olney P.J.S., Mace G.M. & Feistner A.T.C. (eds.), Creative conservation: interactive management of wild and captive animals. Chapman & Hall, London.
Beyer H. 2011: Geo spatial Modelling Environment program, GME v0.4.4. Cited 1 April 2011. www.spatialecology.com
Biggins D.E., Vargas A., Godbey J.L. & Anderson S.H. 1999: Influence of prerelease experience on reintroduced black-footed ferrets (Mustela nigripes). Biol. Conserv. 89: 121-129.
Burt W.H. 1943: Territoriality and home range concepts as applied to mammals. J. Mammal. 24: 346-352.
Connor T., Hull V. & Liu J.G. 2016: Telemetry research on elusive wildlife: a synthesis of studies on giant pandas. Integr. Zool 11: 295-307.
Fabrizio S., Pedrini P. & Marchesi L. 2003: Adaptive selection of foraging and nesting habitats by black kites (Milvus migrants) and its implications for conservation: a multi-scale approach. Biol. Conserv. 112: 351-362.
Hong M.S., Wei W., Yang Z.S. et al. 2016: Effects of timber harvesting on Arundinaria spanostachya bamboo and feeding-site selection by giant pandas in Liziping Nature Reserve, China. For. Ecol Manage. 373: 74-80.
Hong M.S., Yuan S.B., Yang Z.S. et al. 2015: Comparison of microhabitat selection and trace abundance of giant pandas between primary and secondary forests in Liziping Nature Reserve, China: effects of selective logging. Mamm. Biol. 80: 373-379.
Hu J.C., Schaller G.B., Pan W.S. & Zhu J. 1985: The giant panda of Wolong. Sichuan Science and Technology Press, Chengdu, (in Chinese)
Hull V., Roloff G., Zhang J. et al. 2014: A synthesis of giant panda habitat selection. Ursus 25:148-162.
Hull V., Zhang J. & Zhou S. 2015: Space use by endangered giant pandas. J. Mammal. 96: 230-236.
IUCN 2016: The IUCN Red List of Threatened Species, version 2016-2. www.iucnredlist.org
Jule K.R., Leaver L.A. & Lea S.E.G. 2008: The effects of captive experience on reintroduction survival in carnivores: a review and analysis. Biol. Conserv. 141: 355-363.
Kilner Rebecca M., Boncoraglio G., Henshaw J.M. et al. 2015: Parental effects alter the adaptive value of an adult behavioural trait. eLife 4: e07340.
Kleiman D.G. 1996: Reintroduction programs. In: Kleiman D.G., Allen M.E., Thompson K. V. et al. (eds.), Wild mammals in captivity: principles and techniques. University of Chicago Press, Chicago: 297-305.
Kleiman D.G., Stanley Price M.R. & Beck B.B. 1994: Criteria for reintroductions. In: Olney P.J.S., Mace G.M. & Feistner A.T.C (eds.), Creative conservation: interactive management of wild and captive animals. Chapman & Hall Press, New York: 287-303.
Lei M.W., Yuan S.B., Yang Z.S. et al. 2015: Comparison of microhabitats and foraging strategies between the captive-born Zhangxiang and wild giant pandas: implications for future reintroduction. Environ. Sci. Pollut. Res. 22:15089-15096.
Liang Q.W. & Thomson A.J. 1994: Habitat-abundance relationships of the earthworm Eisenia rosea (Savigny) (Lumbricidae), using principle component regression analysis. Can. J. Zool. 72:1354-1361.
Liu J., Chen Y., Guo L.R. et al. 2005: Stereotypic behavior in relation to fecal Cortisol level in captive giant pandas. J. Beijing Normal Univ. (Natur. Sci.) 41: 75-78. (in Chinese)
Nie Y.G., Speakman J.R., Wu Q. et al. 2015: Exceptionally low daily energy expenditure in the bamboo-eating giant panda. Science 349:171-174.
Nussey D.H., Kruuk L.E.B., Morris A. & Clutton-Brock T.H. 2007: Environmental conditions in early life influence ageing rates in a wild population of red deer. Curr. Biol. 17: R1000-R1001.
Pan W.S., Lu Z., Zhu X. et al. 2001: A chance for lasting survival. Beijing University Press, Beijing, (in Chinese)
Schaller G.B., Hu J., Pan W. & Zhu J. 1985: The giant pandas of Wolong. University of Chicago Press, Chicago, IL, U.S.A.
Sebastien S., Perrin N. & Neet C. 2003: Winter habitat selection by two sympatic forest grouse in Western Switzerland: implications for conservation. Biol. Conserv. 112: 373-382.
Short J., Bradshaw S.D., Giles J. et al. 1992: Reintroduction of macropods (Marsupialia: Macropodoidea) in Australia--a review. Biol. Conserv. 62: 189-204.
Soorae P.S. & Stanley Price M.R. 1997: Successful re-introductions of large carnivores--what are the secrets? Paper presented at the 11th International Conference on Bear Research and Management, Graz, Austria.
Stamps J.A. & Swaisgood R.R. 2007: Someplace like home: experience, habitat selection and conservation biology. Appl. Anim. Behav. Sci. 102: 392-409.
State Forestry Administration 2015: Release of the fourth national survey report on giant panda in China. State Forestry Administration, Beijing. http://www.forestry.gov.cn/main/72/content-742880.html
Sun R. Y 2001: Principles of animal ecology, 3rd ed. Beijing Normal University Press, Beijing, (in Chinese)
Wei F.W., Feng Z.J., Wang Z.W. & Hu J.C. 2000: Habitat use and separation between the giant panda and the red panda. J. Mammal. 81: 448-455.
Yong Y, Liu X., Wang T. et al. 2004: Giant panda migration and habitat utilization in Foping Nature Reserve, China. In: Lindburg D. & Baragona K. (eds.), Giant pandas: biology and conservation. University of California Press, Berkeley, CA, U.S.A.
Yu G.Z., Jiang Z.G., Zhao Z.L. et al. 2003: Feeding habitat of giant pandas (Ailuropoda melanoleuca): why do they prefer bamboo patch edges? J. Zool. Lond. 261: 307-312.
Zhang M.C., Huang Y., Li D.S. et al. 2013: Habitat selection of the pre-released giant panda in Wolong Nature Reserve. Acta Ecol. Sin. 33: 6014-6020. (in Chinese)
Zhang Z.J., Zhan X. J., Li Y. et al. 2009: What determines selection and abandonment of a foraging patch by wild giant pandas (Ailuropoda melanoleuca) in winter? Environ. Sci. Pollut. Res. 16: 79-84.
Zhang Z.J., Zhang S.N., Wei F.W. et al. 2006: Translocation and reintroduction of captive giant pandas in China. Acta Theriol. Sin. 26: 292-299. (in Chinese)
Mingchun ZHANG (1), Yan HUANG (1), Mingsheng HONG (2), Shiqiang ZHOU (1), Jinyan HUANG1, Desheng LI (1), Rengui LI (1), Dian LIU (1), Xiaoping ZHOU (1) and Hemin ZHANG (1*)
(1) China Conservation and Research Center for the Giant Panda, Wenchuan 623006, China; e-mail: email@example.com
(2) Genetic Engineering Research Center, Chongqing University, Chongqing 400044, China
Received 11 November 2016; Accepted 10 March 2017
(*) Corresponding Author
Table 1. Information of the pre-released training giant pandas. CN: cub with nature food, MN: mother with nature food, CMF: cub affected by man-made food, MMF: mother with man-made food. CCRCGP: China Conservation and Research Center for the Giant Panda. Name Series number Sex Birthday Natural food group Pre-released cub CN (Taotao) 777 male 2010-8-3 Mother panda MN (Caocao) 581 female 2002 Man-made food group Pre-released cub CMF (Zhangxiang) 826 female 2011-8-20 Mother panda MMF (Zhangka) 505 female 2000 Birth place Natural food group Pre-released cub CCRCGP Mother panda Caopo (wild) Man-made food group Pre-released cub CCRCGP Mother panda Baoxing (wild) Table 2. Description and definitions of variables in the study. Variables Description and definitions Canopy Canopy of overstory in each 20 x 20 [m.sup.2] plot, divided into four categories: [less than or equal to] 25%, 26-50%, 51-75%, and > 75% Slope Slope at microhabitat plots, divided into five categories: 0-10[degrees], 11-20[degrees], 21-30[degrees], 31-40[degrees], and > 40[degrees] Distance from water Distance from water of microhabitat plots, divided into five categories: 0-100 m, 101-250 m, 251-500 m, > 500 m Distance from shelter Distance from shelter of microhabitat plots (m) Grass coverage Canopy of grass in 400 [m.sup.2] microhabitat plot Tree density Number of trees ( > 10 cm in DBH) in each microhabitat plot Shrub density Number of shrubs ([less than or equal to] 10 cm in DBH) in each microhabitat plot Tree dispersion Average distance of the tree in each 100 [m.sup.2] square plot to the center of microhabitat plot Tree DBH Average diameter of trees at the breast height in 400 [m.sup.2] square plot Shrub dispersion Average distance of the shrub in each 100 [m.sup.2] square plot to the center of microhabitat plot Shrub DBH Average diameter of shrubs at the breast height in 400 [m.sup.2] square plot Bamboo coverage Average coverage of bamboos in each control or microhabitat plot Bamboo density Average number of bamboo culms in five 1.0 [m.sup.2] bamboo plots Bamboo height Average height of culms in five 1.0 [m.sup.2] bamboo plots Old shoot density Average number of old shoots in five 1.0 [m.sup.2] bamboo plots Dead bamboo density Average number of dead bamboos in five 1.0 [m.sup.2] bamboo plots Table 3. Independent sample t-test or Mann-Whitney U test for variables among different groups. Variables (*) CN MN 1.94 [+ or -]0.51 Canopy 2.61 [+ or -]1.15 1.84 [+ or -]0.45 Slope 1.65 [+ or -]0.66 2.78[+ or -] 1.18 Distance 1.63 [+ or -]0.71 from water 5.55 [+ or -]2.29 Distance 5.69 [+ or -]2.61 from shelter 16.56 [+ or -]13.49 Grass 16.61 [+ or -]18.31 coverage 12.10 [+ or -]5.25 Tree 11.80 [+ or -]5.36 density 27.50 [+ or -]31.77 Shrub 24.14 [+ or -]13.49 density 3.01 [+ or -]0.74 Tree 3.13 [+ or -]0.57 dispersion 32.61 [+ or -]8.71 Tree DBH 32.90 [+ or -]8.87 Shrub 2.18 [+ or -]0.66 dispersion 2.33 [+ or -]0.54 Shrub DBH 3.30 [+ or -]0.87 Bamboo 2.71 [+ or -]0.53 3.51 [+ or -]0.79 coverage 2.41 [+ or -]0.50 Bamboo 9.60 [+ or -]2.56 density 9.84 [+ or -]1.80 Bamboo 4.31 [+ or -]1.43 height 4.75 [+ or -]0.41 Old shoot 2.95 [+ or -]1.14 density 2.64 [+ or -]1.06 Died bamboo 2.47 [+ or -]0.91 density 2.49 [+ or -]0.65 Variables (*) CMF MMF CN-MN Canopy 2.90 [+ or -]0.67 1.38 [+ or -]0.67 0.58 (0.56) (b) Slope 3.58 [+ or -]0.92 1.95 [+ or -]0.87 -0.57 (0.57) (a) Distance 2.23 [+ or -]0.81 1.19[+ or -]0.60 0.42 (0.67) (b) from water Distance 10.81 [+ or -]6.91 29.14 [+ or -]17.00 0.08 (0.94) (b) from shelter Grass 9.42 [+ or -]9.52 37.33 [+ or -]25.51 -0.01 (0.99) (a) coverage Tree 7.90 [+ or -]4.09 4.17[+ or -] 3.10 0.22 (0.82) (a) density Shrub 14.68 [+ or -]6.48 5.24 [+ or -]5.80 0.55 (0.59) (a) density Tree 2.50 [+ or -]0.45 3.83 [+ or -]1.68 0.75 (0.46) (a) dispersion Tree DBH 38.61 [+ or -]8.46 31.12 [+ or -]9.70 -0.13 (0.90) (a) Shrub dispersion 2.12 [+ or -]0.82 2.62 [+ or -]1.52 -1.00 (0.32) (a) Shrub DBH Bamboo 2.81 [+ or -]1.13 3.26 [+ or -]2.25 -1.03 (0.30) (a) coverage 2.03 [+ or -]0.32 1.33 [+ or -]0.58 0.96 (0.34) (b) Bamboo density 12.29 [+ or -]2.90 6.43 [+ or -]5.73 -0.44 (0.66) (a) Bamboo height 4.71 [+ or -]1.10 1.82 [+ or -]2.02 -1.66 (0.11) (a) Old shoot density 3.33 [+ or -]1.01 1.06 [+ or -]1.25 0.14 (0.26) (a) Died bamboo density 3.11 [+ or -]1.07 1.54[+ or -] 1.33 -0.11 (0.91) (a) t-test or U test Variables (*) CMF-MMF CN/MN- CMF/MMF Canopy 5.63 (0.00) (b) -6.68 (0.00) (b) Slope 6.40 (0.00) (a) -5.59 (0.00) (b) Distance 4.30 (0.00) (b) -4.66 (0.00) (b) from water Distance 4.25 (0.00) (b) 7.20 (0.00) (a) from shelter Grass 3.87 (0.00) (b) -4.49 (0.00) (b) coverage Tree 3.55 (0.001) (a) -4.50 (0.00) (a) density Shrub 4.36 (0.00) (b) -5.15 (0.00) (b) density Tree -4.21 (0.00) (a) 6.49 (0.00) (a) dispersion Tree DBH 2.95 (0.005) (a) -3.66 (0.001) (a) Shrub dispersion -1.37 (0.18) (a) -5.19 (0.00) (b) Shrub DBH Bamboo 0.85 (0.40) (a) -2.99 (0.003) (b) coverage 4.70 (0.00) (b) -6.77 (0.00) (b) Bamboo density 4.33 (0.00) (a) -10.02 (0.00) (a) Bamboo height 4.56 (0.00) (b) -5.96 (0.00) (b) Old shoot density 7.20 (0.00) (a) -10.75 (0.00) (a) Died bamboo density 4.50(0.00) (a) -7.28 (0.00) (a) Table 4. Variables entered into standardized canonical discriminant function. Groups Variables Discriminant coefficients Microhabitat plots Canopy 0.696 selected by CMF and MMF Shrub size 0.330 Shelter distance -0.321 Tree dispersion -0.224 Water distance 0.222 Microhabitat plots Canopy 0.999 between CN/MN-CMF/MMF Shrub dispersion 0.394 Water distance 0.378 Grass coverage -0.257 Table 5. Overall correct prediction results for different plot groups through stepwise discriminant function analysis. Correct prediction Plot groups Total of plots Number of correct prediction plots Microhabitat plots selected by CMF 21 17 Microhabitat plots selected by MMF 31 29 Microhabitat plots of CN/MN 31 31 Microhabitat plots of CMF/MMF 31 28 Correct prediction plots Plot groups Correct prediction percentage Microhabitat plots selected by CMF 80.95 Microhabitat plots selected by MMF 93.55 Microhabitat plots of CN/MN 100 Microhabitat plots of CMF/MMF 90.32 Total correct Plot groups prediction percentage Microhabitat plots selected by CMF 88.46 Microhabitat plots selected by MMF Microhabitat plots of CN/MN 95.16 Microhabitat plots of CMF/MMF
|Printer friendly Cite/link Email Feedback|
|Author:||Zhang, Mingchun; Huang, Yan; Hong, Mingsheng; Zhou, Shiqiang; Huang, Jinyan; Li, Desheng; Li, Rengui|
|Date:||Apr 1, 2017|
|Previous Article:||Predation of montane deserts ungulates by Asiatic cheetah Acinonyx jubatus venaticus in Central Iran.|
|Next Article:||All quiet in the East: molecular analysis retrieves Chionomys layi as part of C. nivalis.|