东北虎豹国家公园东部有蹄类栖息地的灌草层食物资源的量与质

东北虎和东北豹主要捕食马鹿、梅花鹿、狍  及野猪等大中型有蹄类动物,而这些有蹄类的生存依赖森林灌草层的植食性食物资源,形成了东北亚温带森林生态系统完整的啃食食物链 (grazing food chain) 主体。本研究通过对建设中的东北虎豹国家公园东部地区有蹄类栖息地的灌草层植物进行本底调查,获得有蹄类动物的食物资源基线数据。2015年及2016年生长季,在东北虎豹国家公园东部,随机选择141个样地嵌套496条样线,1948个样方,对不同森林结构 (郁闭林及开阔生境,开阔生境包括林窗、林缘和河岸带) 的灌草层植物生物量、食物类别组成 (嫩枝叶、禾莎草、杂类草和蕨类) 及碳、氮含量进行调查分析。研究结果显示：灌草层生物量在开阔生境显著高于郁闭林下 (94.91 g/m² vs. 30.15 g/m²),达到3.15倍。三种开阔生境下的灌草层食物资源类别组成差异显著,在林窗内以嫩枝叶优势,在林缘以杂类草占优势,在河岸带以蕨类占优势。灌草层中杂类草和嫩枝叶平均氮含量高,杂类草碳含量低、C/N低;四类植物热值均超17kJ/g,其中嫩枝叶最高。嫩枝叶、杂类草占优势的高生物量 (生物量大于40 g/m²) 斑块占郁闭林下的16 %、占开阔生境的50 %左右,可能是精食者 (browser) 的取食热点区域。建议在未来国家公园建设中,在合适的地段保留一定的开阔生境,为梅花鹿等食草动物补充高质量的灌草层食物资源斑块,促进有蹄类动物种群发展,并以此为基础恢复虎豹种群。     

东北虎豹生物多样性红外相机监测平台概述

东北虎豹生物多样性红外相机监测平台始建于2006年, 位于中国东北温带针阔混交林区, 覆盖老爷岭、张广才岭和完达山, 面积达1.5万多平方公里。平台的监测目标是从生态系统水平上对东北虎(Panthera tigris altaica)、东北豹(P. pardus orientalis)、有蹄类猎物及同域分布的其他哺乳动物、森林栖息生境、环境要素和人类活动等进行全面系统的调查和观测。截至2019年6月, 平台产生视频记录超过78.5万条, 有效相机工作日173.6万多天, 记录了28种野生兽类和32种野生鸟类。另外, 利用红外相机平台已经在野生动物多样性本底调查、虎豹种群分布、数量与扩散限制、同域食肉动物种间关系、动物生境利用等方面取得一些成果, 同时为东北虎豹国家公园生物多样性监测、评估和管理提供了科技支撑。     

吉林珲春自然保护区东北虎和东北豹及其有蹄类猎物的多度与分布

珲春国家级自然保护区是东北虎(Panthera tigris altaica)、东北豹(Panthera pardus orientalis)等濒危物种在中国的核心分布区。为了探究该区域野生动物的多度水平和空间分布, 了解人类干扰情况, 我们运用相对多度指数(relative abundance index, RAI)分析了2013年4-6月设置于此的83个红外相机位点的监测数据。红外相机的总捕获天数6,060 d, 共捕获10科18种野生哺乳动物, 其中鼬科4种, 猫科动物3种, 犬科、鹿科和松鼠科各2种, 猪科、熊科、麝科、猬科和兔科各1种。研究期间共拍摄到东北虎11只个体, 东北豹13只个体。从相对多度指数来看, 东北虎的相对多度(0.84)远高于东北豹(0.48), 它们的有蹄类猎物中梅花鹿(Cervus nippon)的相对多度最高(2.18), 其次为狍(Capreolus pygargus)(1.53)和野猪(Sus scrofa)(0.92)。人类活动和放牧的相对多度水平(分别为40.64和2.76)显著高于野生动物。在空间分布上, 东北虎和梅花鹿主要在保护区的核心区分布, 且与保护区社区共管区的多度水平差异显著, 而东北豹在不同功能区之间的分布差异不显著, 狍在保护区北部的多度水平较高, 但各功能区之间差异不显著, 野猪在社区共管区的多度水平显著高于核心区。可见, 核心区频繁的人类活动和放牧活动对野生动物的保护产生了影响, 未来应加强关于人类干扰对虎、豹种群及其有蹄类猎物的影响评估。     

辽东山区林权制度改革中林下种植模式对林下植物物种多样性的影响

以样方调查数据为基础,采用物种丰富度指数、均匀度指数和多样性指数,对辽宁省东部山区森林生态系统中种植林下参和大叶芹这两种作物对林下植物物种多样性的影响进行了研究,并分析了不同作物种植样地和未种植样地以及不同种植作物样地之间的各种指数的差异程度。结果表明:(1)种植两种作物均对灌木层物种产生了显著的影响,降低了物种多样性。(2)种植林下参使得草本层的物种丰富度显著降低,均匀度显著增加,而多样性指数差异不显著。(3)种植大叶芹使得草本层的物种丰富度、均匀度和多样性指数均显著降低。(4)林下参种植样地和大叶芹种植样地之间草本层的物种丰富度指数、均匀度指数和多样性指数之间存在显著差异。     

四川白河国家级自然保护区及其周边区域有蹄类多样性与空间分布初报

由于资源分布与环境变量的不同,形成多样的生物多样性分布格局,山地生态系统具有较高的生境异质性和丰富的生物多样性,是研究生物多样性分布的理想选择。为掌握岷山北部有蹄类多样性、分布特征及其影响因素,我们基于四川白河国家级自然保护区及边缘区域的160台红外相机监测数据(2017—2020年),将研究区域按固定间隔划分为5个海拔段,分别计算各海拔段和8种植被类型内有蹄类物种的相对多度指数(RAI)和物种丰富度,整理并初步分析了该区域有蹄类多样性和空间分布。结果显示：(1)该区域共记录到6种有蹄类,毛冠鹿(Elaphodus cephalophus)是优势种,相对多度指数最高(RAI=41.12);其次是中华斑羚(Naemorhedus griseus)(RAI=14.10)和野猪(Sus scrofa)(RAI=6.76),林麝(Moschus berezovskii)(RAI=0.59)和扭角羚(Budorcas taxicolor)(RAI=0.34)最罕见;(2)云杉林和冷杉林中有蹄类物种丰富度均最高(6种),有蹄类相对多度指数则在常绿杜鹃灌丛中最高(RAI=96.86),柏木林内的物种丰富度(2种)和相对多度指数(RAI=19.66)均最低;(3)根据相机监测点的海拔,分为低海拔(< 2 500 m)、中海拔(2 500~2 900 m)和高海拔(> 2 900 m)3组,6种有蹄类可以大致分成3类,即高海拔类群(林麝和扭角羚)、中低海拔类群(毛冠鹿和中华鬣羚)和全海拔类群(中华斑羚和野猪);(4)物种多样性和丰富度在中海拔段均最高,整体呈现近似钟形的分布格局。植被以及植被与海拔的交互效应是影响白河国家级自然保护区有蹄类物种多样性空间分布的主要因素。我们建议：保护区在管理实践中应减少中低海拔段干扰,控制林线以上区域放牧;未来的监测或调查应增加极高海拔区域(3 300 m以上)的抽样强度。     

探讨基于红外相机技术对大型猫科动物及其猎物的种群评估方法

红外相机技术的发展促进了对东北虎(Panthera tigris altaica)、东北豹(Panthera pardus orientalis)及其猎物种群的研究。本研究以珲春保护区春化和马滴达两个区域的监测结果为例, 介绍利用该技术对我国长白山区东北虎、东北豹及其猎物的种群评估方法, 包括监测位点的选择、相机的架设方式及参数设置、数据筛选、东北虎和东北豹体侧花纹个体识别方法、物种相对丰富度的计算以及捕食者与猎物丰富度关系模型的构建。最后就东北虎、东北豹体侧花纹个体识别技术的适用性、红外相机监测与传统调查方法的差异, 相机监测的误差进行了讨论。研究表明, 利用红外相机技术进行密度预测以及东北虎、东北豹个体自动识别技术还需继续完善。1对/25 km²的相机架设密度基本上满足对于珲春保护区春化至马滴达区域虎豹的监测强度要求, 但对于有蹄类则需要另外的监测方案。     

围栏禁牧对内蒙古典型草原群落特征的影响

采用样方法对内蒙古典型草原区围封26 a(E26)7、a(E7)2、a(E2)和未围封(G)样地的植物多样性、群落高度、盖度、地上与地下生物量进行实地调查分析,以研究围栏禁牧对草原植物群落特征的影响.结果表明:围封26a样地具有最高的丰富度指数和多样性指数,围封相对于放牧在一定程度上可以维持和保护植物多样性和丰富度.围封7 a样地的多样性指数与未围封样地(G)以及围封2 a样地(E2)无显著差异,说明放牧导致了该区植物多样性的降低,但围封并未显示出使其恢复的趋势;从自由放牧样地到围封样地,退化指示植物糙隐子草(Cleistogenessquarrosa)以及一年生植物猪毛菜(Salsola collina)、刺穗藜(Chenopodium aristatum)等的比重和出现频率呈减少的趋势;围封2 a样地的地上现存量显著低于围封7 a样地,而围封26 a样地相对于围封7 a样地又表现出显著减小的结果.说明围封在一定时期内可显著提高草地生产力,但围封时间过长将不利于其维持较高的生产力.     

东北虎豹国家公园东部的野猪生境利用和活动节律初步研究

野猪是世界上分布最广的大型哺乳动物之一,也是东北虎豹国家公园内主要的有蹄类动物,东北虎主要的猎物之一。本文采集了中国虎豹观测网络架设在东北虎豹国家公园东部区域的红外相机完整一年的拍摄数据（2015年5月至2016年4月）,通过占域模型和核密度分析,获得不同季节的野猪生境利用情况和日活动节律,探究人为因素、环境因素和生物因素对野猪生境利用的影响。结果显示,野猪偏好于针叶林和针阔混交林,在靠近居民点的区域活动增加。不同物种间的相互作用对野猪的生境利用产生不同影响,受捕食者压力野猪会倾向于躲避东北虎,但东北豹对野猪占域显示为正向影响。梅花鹿和狍对野猪的影响在不同季节呈现相反,梅花鹿对野猪的占域在冬季呈负向影响,而狍对野猪的占域则在夏季呈负向影响。本研究区域内的野猪夏季有2个活动高峰,冬季有1个活动高峰,在不同季节都倾向于白天和晨昏活动,在日落前达到活动最高峰。本研究揭示东北虎豹国家公园东部区域的野猪生境利用和活动节律是受到植被生境、大型食肉动物和人类因素等多种因素相互作用,长期相适应的结果。     

放牧与围栏羊草草原生态系统土壤呼吸作用比较

采用静态箱式法,比较分析了内蒙古典型羊草草原放牧与围栏生态系统土壤呼吸作用及其与环境因子的关系．结果表明,围栏和放牧样地的土壤呼吸作用日动态均呈单峰型曲线,高峰值一般出现在13：00～15：00,围栏样地土壤呼吸作用日动态与地表温度相关性最好,而放牧样地与地下5cm温度相关性最好．在整个观测期内,6、7月份是植物生长的旺盛期,围栏样地土壤呼吸作用明显大于放牧样地约2．7倍;到植物生长后期的8、9月份,二者差异不大,与地下生物量的变化相似,可能与牲畜的采食对不同物候期的植物影响不同及周围环境因子的改变有关,说明人类活动的干扰不一定增加土壤呼吸作用．围栏样地和放牧样地土壤呼吸作用季节动态都与0～10cm的土壤含水量相关性最好,相关系数分别是0．853和0．741,而围栏样地土壤含水量与土壤呼吸作用季节动态的相关性大于放牧样地;围栏和放牧样地不同层次土温、土壤含水量与土壤呼吸作用日、季动态的关系均表现出浅层的相关性普遍大于深层．     

放牧对若尔盖高原湿地CH4排放的影响

湿地是大气甲烷(CH_4)的主要排放源,而有关放牧对湿地CH_4排放的影响特征仍未得到足够的报道。因此,通过静态箱法,研究了放牧对四川省若尔盖高原湿地CH_4排放的影响,CH_4气体通过快速温室气体分析仪测量。结果表明:放牧样地和围栏内样地生长季CH_4排放量为(31.32±19.57)g/m~2和(30.31±23.46)g/m~2,它们之间无差异显著;但是集中放牧期间(7—9月),放牧样地(21.01±12.35)g/m~2较围栏内样地显著增加了CH_4排放量为54.3%。2014年生长季期间通过刈割植物模拟放牧表明两种刈割强度CH_4排放量为(5.01±5.37)g/m~2和(4.69±5.99)g/m~2,较未刈割样地(1.15±1.89)g/m~2增加了335.9%和308.0%,其原因可能是放牧或者刈割减少地表植物生物量,降低植物高度,缩短了CH_4排放的路径距离。该结果可为我国高原湿地保护与管理决策提供基础数据支撑。     

东北虎豹国家公园森林声景的昼夜和季节变化

被动声学监测技术和声学指数通过对音频数据的时频域特征进行定量分析,可以反映声景的复杂度、多样性和健康程度等,已经成为评估生物多样性变化的重要手段。本研究从2020年6月至2021年6月在东北虎豹国家公园采集了52个点的声学数据,计算了春、夏、秋、冬4个季节和黎明、白天、黄昏、夜晚4个昼夜时间段的声音复杂度指数(acoustic complexity index,ACI)、声音多样性指数(acoustic diversity index,ADI)、声音均匀度指数(acoustic evenness index,AEI)、生物声学指数(bioacoustic index,BIO)、标准化声景差异指数(normalized difference soundscape index,NDSI)、声音熵指数(acoustic entropy index,H)和1–21k Hz共20个频段的功率谱密度(power spectral density,PSD)等声学指数,评价了声景构成和多样性的昼夜和季节性差异。结果表明,东北虎豹国家公园的声景随季节变化具有显著的昼夜节律差异,尤其是夜晚的声景和声学成分...     

Changes in composition and structure of a tropical dry forest following intermittent cattle grazing

In northwestern Costa Rica, cattle are being used as a "management tool" to reduce the amount of combustible material, mainly dominated by Hyparrhenia rufa, an African grass. This project is being developed within Parque Nacional Palo Verde and Reserva Biológica Lomas Barbudal, both of which form part of the only remaining tropical dry forests in Mesoamerica. To determine the short-term effects of cattle grazing on the natural vegetation, we compared the floristic composition within Palo Verde in an area under intermittent cattle grazing with an area that has not been grazed. There were significantly fewer plant species in the area with intermittent cattle grazing compared to the area with no grazing. Floristic composition of these two habitats was different as reflected by both Fisher's alpha values and the Shannon index of diversity, both of which were significantly higher in the ungrazed site. The ungrazed area contained more plant species and was more similar to mature forest. The structure of the vegetation was significantly different between the intermittently grazed and ungrazed sites with more small stems (1-5 cm dbh) and fewer large stems (> 5 cm dbh) in the intermittently grazed habitat. These results indicate that cattle grazing has an impact on the dry forest by reducing the relative abundance and density of larger tree species and by changing the species composition and structure of the community. The current management plan implemented in Palo Verde and Lomas Barbudal is not appropriate because of the impact that cattle have on the structure of the natural vegetation and should not be considered a viable alternative in other protected areas of dry forest in the Neotropics. We suggest that alternative fire prevention measures be evaluated including hand-cutting H. rufa, the creation of more frequent and larger fire breaks, and the development of green breaks.     

Effects of grazing and cultivation on forest plant communities in Mount Elgon National Park, Uganda

Plant communities in the montane forest of Mount Elgon National Park were studied in order to assess the impact of grazing and cultivation on species composition. Present and former land uses, tree, shrub and herb species, soil properties and the percentage cover and height of trees, shrubs and herbs were determined in 40 plots. An indirect ordination of these plots showed that species composition was primarily determined by successional stage and agricultural disturbance. In forest plots (ordinated separately) where the widest range of former and current grazing intensities had occurred, evidence of grazing history, soil phosphorus and vegetation height correlated negatively with the strongest ordination axis. Least grazed forest plots had fewer tree seedlings and saplings than more intensively grazed plots. This may be due to the increase in Mimulopsis alpina (Acanthaceae) in less grazed forest where tree regeneration might otherwise be more advanced. Tree seedlings and saplings were uncommon in the forest, rarely exceeding 30cm in height and there was no tree understorey. Although grazing is important for preserving species diversity in Mount Elgon National Park through the maintenance of species-rich grasslands, long-term effects on montane forest communities must be considered in future park management.     

东北虎豹国家公园梅花鹿的空间遗传格局及其影响因素

东北梅花鹿是东北虎豹国家公园主要的大型食草动物之一,是东北虎豹的主要猎物,对针阔混交林群落的维持有关键的作用,探究其遗传多样性及空间遗传格局对东北梅花鹿的保护以及国家公园生态系统的健康至关重要。在国家公园珲春保护区内,通过非损伤方法获得遗传样本,利用微卫星标记,研究该梅花鹿种群的空间遗传格局及其影响因素。结果表明：本研究区梅花鹿种群平均期望杂合度为0.721,遗传多样性较为丰富。有限的扩散能力常常导致种群在遗传距离上具有显著的空间自相关模式,本研究区梅花鹿种群在0-1km距离等级内在遗传距离上具有显著的空间自相关现象,据此可推测,该地区梅花鹿扩散距离为1km左右。STRUCTURE分析表明,珲春地区梅花鹿种群不存在明显的遗传分化。各种空间变量可以显著影响物种的遗传分化。本研究选取海拔、坡度、坡向、地表起伏率、人类干扰5个变量,研究其对梅花鹿种群遗传结构的影响,这5个变量多被认为与大中型哺乳动物扩散阻碍相关。依据5个变量建立了336个阻力模型,并进行偏曼特尔检验。其中,依据海拔、坡向、地表起伏率、人类干扰假设建立的246个阻力模型与遗传距离之间的关系并不显著,综合所有变量的15个生境适宜性模型阻力模型与遗传距离的关系也都不显著。在依据坡度假设建构的75个阻力模型中,只有1个模型与遗传距离有显著的正相关关系,该模型同时也是在控制空间自相关影响后,在所有模型中与遗传距离相关性最高的模型。根据该模型推测,最适宜梅花鹿扩散的坡度为10°,梅花鹿可能倾向于利用缓坡进行扩散。结果对东北虎豹国家公园梅花鹿种群的保护具有重要意义。     

Effects of bison and cattle on growth, reproduction, and abundances of five tallgrass prairie forbs

Forb populations were sampled on Kansas tallgrass prairie to examine the effects of native (bison) and domestic (cattle) ungulates on plant growth, reproduction, and species abundances. Five locally and regionally abundant native tallgrass prairie perennials, Baptisia bracteata, Oenothera speciosa, Vernonia baldwinii, Solidago missouriensis, and Salvia azurea, were selected for study. Replicate watershed-level treatments included three grazing regimes (ungrazed, grazed by cattle, and grazed by bison), and two spring fire frequencies (annually burned and burned at 4-yr intervals). The results show that forb responses to ungulates in tallgrass prairie are complex and vary significantly among plant species, ungulate species, fire regimes, and plant life history stages. Some forbs (e.g., B. bracteata, O. speciosa, and V. baldwinii) increased in growth and reproduction in grazed sites, indicating competitive release in response to selective grazing of the dominant warm-season matrix grasses. Forbs that reduced performance in grazed sites are likely negatively affected by disturbances generated by ungulate nongrazing activities, because none of the forbs studied were directly consumed by bison or cattle. Large grazers had no detectable effect on the frequency of plant damage by other herbivores or pathogens. Significant effects of grazers on patterns of flowering and seed production were not congruent with their effects on population densities, indicating that variation in sexual reproduction plays a minor role in regulating local population abundances. Furthermore, the native and domestic ungulates differ significantly in their effects on forb growth and reproduction.     

Impact of Red Deer Cervus elaphus Grazing on Bilberry Vaccinium myrtillus and Composition of Ground Beetle (Coleoptera, Carabidae) Assemblage

We studied the role of red deer Cervus elaphus L. as ecosystem modifier in boreal forest (Tingvoll municipality, 62°52′ N, 8°20′ E, Norway), during early summer of 2001. The effect of grazing by red deer on ground beetles (Carabidae) abundance and diversity was investigated across a gradient of grazing pressures. We trapped ground beetles by pit-fall traps from three homogeneous winter grazing areas (ungrazed, medium grazed, heavily grazed). Bilberry Vaccinium myrtillus (the main winter food for red deer) was sampled and its dry weight was measured for the three locations. Gradient analyses showed that grazing by red deer affects carabid species composition. Grazing significantly affected the amount of bilberry, which correlated with species variation. According to our predictions, we found a higher abundance of carabids in the heavily grazed location, but the species richness and the diversity indices were similar for the three areas. This study shows that overall species composition is altered along a gradient as consequence of red deer winter grazing and that red deer act as ecosystem engineer, by reducing the bilberry heather which dominates the field layer in early summer.     

Effects of introduction and exclusion of large herbivores on small rodent communities

In this study we analysed the effects of large herbivores on smallrodent communities in different habitats using large herbivore exclosures. Westudied the effects of three year grazing introduction by red deer(Cervus elaphus L.) in previously ungrazed pine and oakwoodland and the exclusion of grazing by red deer, roe deer(Capreoluscapreolus L.) and mouflon (Ovis ammon musiminL.) in formerly, heavily grazed pine woodland and heathland. At eight exclosuresites within each habitat type, small rodents were captured with live trapsusing trapping grids. At each trapping grid, seed plots of beechnuts(Fagus sylvatica L.) and acorns (Quercusrobur L.) were placed to measure seed predation by rodents.Exclusion of grazing by large herbivores in formerly, heavily grazedhabitats had a significant effect on small rodent communities. Insideexclosureshigher densities of mainly wood mice (Apodemus sylvaticusL.) and field voles (Microtus agrestis L.) were captured.Introduction of grazing by red deer appeared to have no significant negativeeffects on small rodent communities. The seed predation intensity of beechnutsand acorns by small rodents was significantly higher in ungrazed situations,particularly in habitats that were excluded from grazing. The differencesbetween grazing introduction and exclusion effects on small rodent communitiescan be explained by differences in vegetation structure development. Therecovery of heavily browsed understory vegetation after large herbivore grazingexclusion proceeded faster than the understory degradation due to grazingintroduction. Small rodents depend on structural rich vegetations mainly forshelter. We conclude that large herbivores can have significant effects onvegetation dynamics not only via direct plant consumption but also throughindirect effects by reducing the habitat quality of small rodent habitats.