卡拉麦里山有蹄类自然保护区蒙古野驴生境适宜性评价

为加强蒙古野驴(Equus hemionus hemionus)的生境保护及管理工作,作者以2005年以来在卡拉麦里山有蹄类自然保护区的野外调查数据为基础,在地理信息系统(GIS)支持下,以距水源点距离、坡度、植被类型和人类活动为评价因子,采用生境评价模型,对蒙古野驴的生境进行了适宜性评价。不考虑人类活动影响下,春、夏、秋、冬四季潜在总适宜生境面积分别为9,784km2、8,090km2、9,379km2和10,856km2,分别占保护区总面积的54.4%、44.9%、52.1%和60.3%。由于受到国道、矿产开采、冬季放牧等人类活动的强烈影响,研究区内适宜生境大量丧失,冬季丧失面积最多,为6,629km2,占冬季潜在总适宜面积的61.1%。基于评价结果作者提出了相应的蒙古野驴种群保护措施:(1)加强水源地的保护;(2)限制冬季进入保护区内家畜的数量,并为蒙古野驴划定预留适宜生境;(3)严格制定进入保护区的制度;(4)拆除迁移路线上的边境围栏或建设野生动物通道,以保障蒙古野驴正常的迁徙活动,恢复其种群基因交流。     

蜂桶寨自然保护区大熊猫生境适宜性评价与保护管理对策

对濒危野生动物而言,开展生境质量评价是完善就地保护措施、提高自然保护成效的基础。蜂桶寨自然保护区位于邛崃山系中段,是大熊猫模式标本的采集地。而此前有关该保护区大熊猫生境的研究主要集中在生境的选择上,生境适宜性评价方面的研究尚未开展。本文以海拔、坡度、植被类型、食物来源等4个生态因子为指标,通过构建景观连接度模型对保护区内大熊猫生境适宜性进行评价。结果表明,保护区内大熊猫不适宜生境面积、较适宜生境面积及最适宜生境面积分别为223.26、133.67和33.46 km2,分别占保护区总面积的57%、34%和9%。从空间分布来看,最适宜生境和较适宜生境在保护区内的分布较为破碎分散,大熊猫活动痕迹点更多地集中在生境适宜程度较高的区域。为加强该区大熊猫种群的科学保护,应控制敏感区域的人为活动,确保保护区内大熊猫个体在不同生境斑块之间迁移扩散。日常保护管理工作中应重点关注与黄水河自然保护区相连区域,并可适度扩大蜂桶寨自然保护区的管护范围。     

森林采伐对桃红岭国家级自然保护区梅花鹿冬季生境选择的影响

2011年和2012年的冬季在桃红岭国家级自然保护区采用随机样方法,调查了森林采伐对梅花鹿冬季生境选择的影响。调查结果表明:梅花鹿冬季在采伐迹地和非采伐区生境选择存在显著性差异。在采伐迹地,梅花鹿多在植被密度适中或稠密、覆盖度适中或较高、海拔200 m以上的生境活动;在非采伐区,梅花鹿多在植被高度低于1 m、植被密度适中、海拔400 m以上的生境活动。森林采伐后第3年梅花鹿的活动利用强度最大。     

甘肃大熊猫生境质量评价

本研究以第四次大熊猫(Ailuropoda melanoleuca)调查、甘肃省森林资源二类清查等数据为基础资料,依据国内外有关大熊猫对生境选择利用的研究成果,结合本地本山系大熊猫分布及活动的实际情况,选取竹子分布、植被类型、海拔、坡度、坡向、道路和居民区等评价因子,建立了大熊猫生境质量评价指标体系和准则,借助Arcgis10.2软件,利用栅格赋值和空间叠加原理系统地研究了甘肃大熊猫生境质量。结果表明,甘肃大熊猫生境质量总体较好,适宜和较适宜生境面积总和占到了69.77%;四个局域种群单元中白水江单元适宜生境面积最大,其次为甘南单元;各大熊猫分布县中,文县的大熊猫生境质量最好,其次为舟曲;甘肃大熊猫适宜生境大都处于保护区中,各保护区适宜生境总和为178 771 hm~2,占全省大熊猫适宜生境的88.72%;各保护区中,白水江国家级自然保护区的适宜生境面积最大,其次为插岗梁省级保护区。     

基于鹤群数量和活动时间的白头鹤越冬生境分级

崇明东滩作为国家级鸟类自然保护区,是国家重点保护鸟类白头鹤(Grus moracha)重要的越冬栖息地,但近年来由于人类活动加剧以及外来物种互花米草(Spartina alterniflora)影响,白头鹤种群的越冬适宜生境也随之变化,给白头鹤种群的保护及区域环境保护带来严峻挑战。本文从4种重要的生境因子(覆被类型、植被盖度、淹水深度、大堤距离)着手,研究了环境变量对鹤群行为方式的影响,并且利用鹤群数量以及鹤群活动时间作为参比标准对环境因子的适宜性进行量化。结果表明:白头鹤在崇明东滩的适宜越冬生境面积为697 hm2,次适宜生境面积为469 hm2,微适宜生境面积为282 hm2,非适生境面积352 hm2,白头鹤适宜生境和非适生境面积占区域总面积的38.7%和19.6%,其余生境超过区域总面积40%。白头鹤在崇明东滩堤外的潜在适宜生境面积比重较大,这为扩展鹤群的适宜生境面积提供了可能。文章提出了关于白头鹤种群保护及扩大鹤群适宜生境面积的措施及办法:在次适宜和微适宜生境区投放饵料以扩大其适宜生境面积,同时加大对本土物种海三棱藨草(Scirpus mariqueter)的恢复力度。     

青海湖东-克图地区普氏原羚生境适宜性评价

普氏原羚(Procapraprzewalskii)是我国特有珍稀濒危动物,历史上曾分布于我国的内蒙古、甘肃、宁夏和青海等地,现仅分布在青海湖周边地区。作者通过2002–2004年不同季节的实地调查,在地理信息系统(GIS)的支持下,以可食植物丰富度、坡度、隐蔽条件和人类活动等为评价因子,采用生境评价模型,对普氏原羚的主要分布区之一青海湖东-克图地区进行了适宜性评价。评价结果表明,不考虑人类活动影响时普氏原羚的适宜和次适宜生境面积分别为2493.76hm2和18624.06hm2,分别占研究区总面积的8.05%和60.15%;考虑人类活动影响时,普氏原羚的适宜和次适宜生境面积分别减少了5.81%和33.09%,而不适宜生境面积增加了38.90%。由于普氏原羚的生境受到居民地、道路、围栏等人类活动的强烈影响,导致大量适宜生境丧失,生境隔离和破碎化日益加剧,建议重新规划保护区,将普氏原羚的适宜生境划入保护区的核心区;建立生境廊道,拆除部分围栏,以提高普氏原羚的生境质量,促进其种群的发展。     

卡拉麦里山有蹄类自然保护区鹅喉羚生境适宜性评价

在卡拉麦里山保护区内选取具有代表性的研究样区约1 447 km² 作为评价区,基于2005 年以来对卡拉麦里山有蹄类自然保护区鹅喉羚野外调查和样方采集,利用模糊赋值法建立生境评价模型,结合GIS 技术的空间分析功能,以植被类型、坡度、坡向和人类干扰活动为评价因子进行生境适宜性研究。结果表明:春、夏、秋、冬四季实际生境面积分别为 1146.9km² 、1137.1 km² 、991.6 km² 和499.8 km² ,分别占研究区域总面积的79.3% 、78.6% 、68.5% 和34.5% ;其中适宜生境面积分别为304.1 km² 、599.4 km² 、303.6 km² 和56.2 km² ,分别占研究区域总面积的21.0% 、41.4% 、21.0% 和3.9% 。人类活动影响下,一些潜在生境转变为不适宜生境,春、夏、秋、冬四季生境分别丧失4.0% 、3.1% 、4.3% 和48.5%。在各种人类活动中,居民点、国道、采矿点对鹅喉羚生境具有一定的干扰作用,使其质量有所降低,但未造成严重影响;而冬季牧民的放牧行为,导致鹅喉羚的适宜生境被家畜占据,鹅喉羚生境质量大面积下降。本文基于评价结果提出了保护措施。     

基于MAXENT模型的古田山保护区黑麂生境适宜性评价

浙江开化古田山国家级自然保护区是黑麂（Muntiacus crinifrons）的集中分布区之一。近年来,保护区内黑麂面临着生境丧失和破碎化的威胁。本研究应用MAXENT模型,结合古田山保护区2014-2017年的红外相机监测数据和主要环境变量数据,对保护区内黑麂生境适宜性的季节变化特征及影响因素进行了评价与分析。结果表明：距阔叶林距离、海拔两个变量对黑麂生境适宜性的季节性变化影响最为显著。古田山保护区不同季节黑麂的适宜生境面积为：春季2086.38 hm²、夏季2608.74 hm²、秋季2502.27 hm²和冬季1746.27 hm²,分别占保护区总面积的25.74%、32.18%、30.87%和21.54%。从空间分布来看,黑麂适宜生境主要分布在保护区的核心区和北部区域。建议加强对保护区的核心区和北部区域自然植被的保护与恢复,以及对保护区人为干扰活动的监督和管理。     

基于MaxEnt模型的九寨沟国家级自然保护区川金丝猴适宜生境研究

川金丝猴Rhinopithecus roxellana是我国特有的灵长类重点保护物种,九寨沟国家级自然保护区是其分布区之一。利用MaxEnt模型对九寨沟国家级自然保护区川金丝猴生境进行研究,结果显示:(1) MaxEnt模型的预测准确度极高,训练集受试者工作特征曲线下面积达到0. 981±0. 011;(2)保护区内川金丝猴的适宜生境面积为7 519. 68 hm2,占保护区总面积的11. 7%,主要分布在北部的林地中;(3)根据贡献率、置换重要值和Jackknife检验,影响川金丝猴分布的最主要环境因子是海拔和距公路距离,植被型、坡向和距步道距离的影响次之,其他环境因子的影响较小;(4)川金丝猴适宜生境的海拔为2 100~3 500 m,距公路和步道距离分别为700~5 000 m和150~3 500 m,位于南坡、西南坡、西坡和西北坡的寒温性针叶林、温性针叶林、针阔混交林和落叶阔叶林中。根据分析结果,建议减少人类活动对川金丝猴的干扰,加强对保护区边缘地域的生境保护,确保川金丝猴适宜生境与周边地区的连通性。     

岷山地区大熊猫生境评价与保护对策研究

综合运用大熊猫生物学与行为生态学研究成果、遥感数据分析与地理信息系统技术 ,在系统研究岷山地区大熊猫生境分布、生境质量与空间格局的基础上 ,明确岷山地区保护大熊猫的关键区域 ,分析岷山地区大熊猫保护与自然保护区建设的对策 ,以期为岷山地区大熊猫保护及其与岷山地区资源开发与发展的协调提供依据。遥感数据分析结果表明 ,岷山地区以森林为主 ,各类森林面积 1 91 790 3.4 4 hm2 ,占 5 5 .4 2 % ,将与大熊猫生境密切相关的森林植被分为常绿阔叶林、落叶阔叶林、针阔混交林、亚高山针叶林等 ,其中亚高山针叶林面积 5 380 4 9.6 4 hm2 ,占全部森林的占 2 8.0 5 % ,落叶阔叶林面积 4 6 1 35 5 .6 7hm2 ,占2 4 .0 6 % ,针阔混交林面积 4 0 30 36 .2 6 hm2 ,占 2 1 .0 1 %。结果表明岷山地区有大熊猫潜在生境 1 32 3789.1 5 hm2 ,由于森林资源利用、交通、农业活动影响、居民薪柴砍伐 ,以及生境破碎化与生境隔离等导致的生境丧失 5 5 341 3.4 5 hm2 ,目前尚存的大熊猫适宜生境 770 375 .7hm2 ,由于交通等隔离而成为至少 5个相互分隔的生境单元 ,大熊猫种群交流受到严重阻碍。为了有效地保护岷山大熊猫 ,首先应充分注意到各种人类活动 ,尤其交通的建设对大熊猫生境的影响 ;其次要扩大自然保护区范围 ,     

Habitat suitability assessment of Sichuan sika deer in Tiebu Nature Reserve during periods of green and dry grass

Habitat suitability assessment is an essential and dynamic research method for determining and evaluating the environmental pressures faced by wildlife. From March to November 2011, we investigated the quality of habitat available to Sichuan sika deer (Cervus nippon sichuanicus) in Tiebu Nature Reserve, Ruoergai County, Sichuan Province, China. A habitat evaluation model established by the fuzzy assignment quadrature method was used to assess habitat suitability for Sichuan sika deer within the reserve by using the GIS spatial analysis function. The results showed that the area of actual available habitat was 220.8 km² during the wet season and 213.2 km² during the dry season, accounting for 80.8% and 78.02% of the total nature reserve area, respectively. The area of suitable habitat for Sichuan sika deer was much lower, 128.01 km² during the wet season and 109.17 km² during the dry season, accounting for 46.84% and 39.95% of the total nature reserve area respectively. The difference between available and suitable habitat is likely due to potentially good habitat having been lost as a result of human disturbance. Lost habitat makes up 4.55% of the total area while grass is green and 5.52% while grass is dry. Human disturbance levels in the form of roads and residential areas were constant throughout the year, but grazing by domestic animals had a higher impact during the dry season. Habitat suitability during this time, already reduced by the withering of the grass, was thus further reduced by the grazing of livestock.     

江西桃红岭自然保护区夏季梅花鹿对生境的选择性

2005年6-8月在江西桃红岭自然保护区对夏季梅花鹿的生境选择性进行了初步研究。结果表明：梅花鹿选择灌丛和灌草丛、郁闭度较低、灌木盖度较小、食物丰富度高、阴坡、中上坡位、坡度平缓、水源距离在100-400m、人为干扰距离〉800m和海拔高度〉300m的环境;对郁闭度〉80％和水源距离≤100m的环境表现为随机选择。     

基于MAXENT模型的丹顶鹤营巢生境适宜性分析——以扎龙保护区为例

明确物种繁殖栖息地的潜在分布对于受胁物种的保护与科学管理具有十分重要的意义。扎龙保护区是国际濒危物种丹顶鹤西部迁徙种群的主要繁殖地之一,近年来繁殖种群数量波动较大。通过GIS空间技术平台,利用MAXENT模型,结合2012—2013年丹顶鹤(Grus japonensis)营巢分布点和环境特征变量,对扎龙保护区丹顶鹤营巢生境的适宜性进行了分析。结果表明:模型的评价效果达到优秀水平(训练集AUC=0.901);绿度(34.9%)、距道路距离(17.1%)、土壤湿度(16.3%)、海拔(15.7%)是丹顶鹤营巢生境的主要环境特征变量;核心区中部和南部是丹顶鹤主要的适宜营巢分布区,缓冲区和实验区有少量的适宜营巢区分布,丹顶鹤适宜营巢生境面积为35857.35hm~2,占保护区总面积的17.07%。建议在重点管理核心区的同时,对缓冲区和实验区的小面积芦苇沼泽给予更多关注。     

Home range and habitat use of male Reeves’s pheasant (Syrmaticus reevesii) during winter in Dongzhai National Nature Reserve, Henan Province, China

Home range and habitat use of male Reeves’s pheasant (Syrmaticus reevesii) were studied during winter of 2001～2002 and 2002～2003 in the Dongzhai National Nature Reserve, Henan Province. Results from five individuals of Reeves’s pheasant with over 30 relocations, indicated that the average size of home range was 10.03 ± 1.17 hm² by Minimum Convex Polygon method, 8.60 ± 0.35 hm² by 90% Harmonic Mean Transformation method, and 9.50 ± 1.90 hm² by 95% Fixed Kernel method. It was observed that the winter range is smaller than that in the breeding season. The mean core area of the home range was found to be 1.88 ± 0.37 hm². Although the habitat composition of the core area varied greatly for individuals, a large part of the habitats used were composed of confier and broadleaf mixed forests, masson pine forests, fir forests, and shrubs. Habitat use within the study area was non-random, while habitats within home ranges were randomly used. Habitat use was dictated by tree diameter at breast height, shrub height and coverage at 2.0 m. The proximity between forests and shrubs were also found to be important in providing refuge for the birds during winter. Recommendations for conservation management include protecting the existing habitats in Dongzhai National Nature Reserve, increasing suitable habitat for Reeves’s Pheasant through artificial plantations (e.g. firs), and restoring some parts of the large shrub area into forests.     

基于最大熵模型的野生马麝夏季生境适宜性研究

野生马麝(Moschus chrysogaster)是珍稀濒危资源动物,分布于我国青藏高原及周边地区。甘肃兴隆山国家级自然保护区是野生马麝最重要的分布区之一,深入了解保护区的生境结构、质量及分布是对区域内野生马麝进行成功保护的前提和基础,但迄今缺乏大尺度的马麝生境适宜性研究。利用实地调查得到的兴隆山保护区的野生马麝夏季分布点数据,采用最大熵(MaxEnt)模型,结合地形、归一化植被指数、距河流距离、距道路距离等环境变量数据,进行野生马麝的夏季生境适宜性分析。结果表明：影响野生马麝夏季生境适宜性的主要生态因子是海拔、坡向、植被和河流,其贡献率分别达40.3%,23.4%,18.6%和10.9%;兴隆山保护区野生马麝的夏季潜在适宜生境分布面积为123.34 km²,占整个保护区的41.11%,占保护区林地的61.92%;野生马麝夏季潜在适宜生境主要集中在保护区的中部和西部,其中高适宜性生境约为保护区的4.47%,各适宜区间及适宜区之内均存在一定程度的不连续分布。为加强对兴隆山保护区野生马麝种群及生境的就地保护,建议通过生境保育措施,提高野生马麝潜在分布区的生境适宜性,...     

浙江清凉峰国家级自然保护区华南梅花鹿栖息地适宜性评价

理解环境因子对物种空间分布的影响,评价栖息地适宜性现状并预测潜在分布区,对野生动物的管理和保护具有重要意义。华南梅花鹿（Cervus pseudaxis）属国家I级重点保护野生动物,现仅分布于安徽、浙江、江西等狭小片区内。浙江清凉峰自然保护区千顷塘区域是华南梅花鹿的重要分布区,但其面积较小,严重限制了华南梅花鹿的种群发展,亟需对千顷塘及周边区域的栖息地质量进行评价,为华南梅花鹿的保护和野外放归提供科学依据。本研究利用红外相机监测千顷塘区域华南梅花鹿的分布,结合遥感等技术手段获得地形、植被、水源以及人为干扰等8种环境因子,利用MaxEnt构建华南梅花鹿栖息地适宜性模型,对以千顷塘为中心50 km×50 km的范围进行栖息地适宜性评价。研究结果表明,华南梅花鹿倾向于选择海拔1050-1240 m范围内,距道路100-900 m和距人口聚居区3200-3800 m的相对平缓地带。千顷塘区域华南梅花鹿栖息地保护较好,适宜栖息地面积为2224 hm2,占该区域39.1%。千顷塘周边适宜性较高的区域主要为位于其西南部约10 km的山区,该区域为华南梅花鹿提供了3253 hm2的潜在适宜栖息地。建议降低保护区千顷塘区域内的人为干扰,并在其西南部山区尝试开展圈养种群的野外放归工作,以促进其种群发展。     

Home range and habitat use of male Reeves’s pheasant (Syrmaticus reevesii) during winter in Dongzhai National Nature Reserve, Henan Province, China

Home range and habitat use of male Reeves’s pheasant (Syrmaticus reevesii) were studied during winter of 2001∼2002 and 2002∼2003 in the Dongzhai National Nature Reserve, Henan Province. Results from five individuals of Reeves’s pheasant with over 30 relocations, indicated that the average size of home range was 10.03 ± 1.17 hm² by Minimum Convex Polygon method, 8.60 ± 0.35 hm² by 90% Harmonic Mean Transformation method, and 9.50 ± 1.90 hm² by 95% Fixed Kernel method. It was observed that the winter range is smaller than that in the breeding season. The mean core area of the home range was found to be 1.88 ± 0.37 hm². Although the habitat composition of the core area varied greatly for individuals, a large part of the habitats used were composed of confier and broadleaf mixed forests, masson pine forests, fir forests, and shrubs. Habitat use within the study area was non-random, while habitats within home ranges were randomly used. Habitat use was dictated by tree diameter at breast height, shrub height and coverage at 2.0 m. The proximity between forests and shrubs were also found to be important in providing refuge for the birds during winter. Recommendations for conservation management include protecting the existing habitats in Dongzhai National Nature Reserve, increasing suitable habitat for Reeves’s Pheasant through artificial plantations (e.g. firs), and restoring some parts of the large shrub area into forests. __________ Translated from Biodiversity Science, 2005, 13 (5) [译自: 生物多样性, 2005,13(5)]     

Habitat Assessment for Giant Pandas in the Qinling Mountain Region of China

ABSTRACT Because habitat loss and fragmentation threaten giant pandas (Ailuropoda melanoleuca), habitat protection and restoration are important conservation measures for this endangered species. However, distribution and value of potential habitat to giant pandas on a regional scale are not fully known. Therefore, we identified and ranked giant panda habitat in Foping Nature Reserve, Guanyinshan Nature Reserve, and adjacent areas in the Qinling Mountains of China. We used Mahalanobis distance and 11 digital habitat layers to develop a multivariate habitat signature associated with 247 surveyed giant panda locations, which we then applied to the study region. We identified approximately 128 km²of giant panda habitat in Foping Nature Reserve (43.6% of the reserve) and 49 km²in Guanyinshan Nature Reserve (33.6% of the reserve). We defined core habitat areas by incorporating a minimum patch-size criterion (5.5 km²) based on home-range size. Percentage of core habitat area was higher in Foping Nature Reserve (41.8% of the reserve) than Guanyinshan Nature Reserve (26.3% of the reserve). Within the larger analysis region, Foping Nature Reserve contained 32.7% of all core habitat areas we identified, indicating regional importance of the reserve. We observed a negative relationship between distribution of core areas and presence of roads and small villages. Protection of giant panda habitat at lower elevations and improvement of habitat linkages among core habitat areas are important in a regional approach to giant panda conservation.     

华南梅花鹿主雄的社会行为初步研究

2005年3～12月,在江西桃红岭自然保护区对华南梅花鹿主雄的社会行为进行了初步研究,记录了主雄等级序位的建立与维持、声音通讯、领域性、争雌打斗、交配和护群等6类社会行为,并对这些行为的生物学意义进行了初步分析.     

Application of ecological-niche factor analysis in habitat assessment of giant pandas

Ecological-niche factor analysis (ENFA) is a multivariate approach to study geographic distribution of species on a large scale with only “presence” data. It has been widely applied in many fields including wildlife management, habitat assessment and habitat prediction. In this paper, this approach was applied in habitat suitability assessment for giant pandas in Pingwu County, Sichuan Province, China. With “presence” data of giant pandas and remote sensing data, habitat suitability of pandas in this county was evaluated based on ENFA model, and spatial distribution pattern of nature reserves and conservation gaps were then evaluated. The results show that giant pandas in this county prefer high-elevation zones (> 2128 m) dominated by coniferous forest, and mixed coniferous and deciduous broadleaf forest, and avoid deciduous broadleaf forest and shrubs. Pandas avoid staying at habitats with human disturbances. Farmland is a major factor threatening panda habitat. Panda habitat is mainly distributed in north and west of Pingwu with a total area of 234033 hm², 106345hm² for suitable habitat and 127688 hm² for marginally suitable habitat). 3 nature reserves were located in Pingwu, covering over 49.2% of total suitable habitat and 45.6% of total marginally suitable habitat. Although 47.2% of panda habitat was in reserves under protection, connectivity between reserves was weak and a conservation gap existed in the north part of Pingwu. Thus, a new nature reserve in Baima and Mupi should be established to link the isolated habitats.