伊犁和塔城地区新疆野苹果种群结构及动态特征
作者:
作者单位:

作者简介:

通讯作者:

中图分类号:

基金项目:

第三次新疆综合科学考察项目(2021xjkk1200,2021xjkk1203-09,2021xjkk1205)


Population structure and dynamic characteristics of Malus sieversii distributed in Ili and Tacheng regions of Xinjiang, China
Author:
Affiliation:

Fund Project:

the Third Xinjiang Scientific Expedition Program (2021xjkk1200, 2021xjkk1203-09, 2021xjkk1205)

  • 摘要
  • |
  • 图/表
  • |
  • 访问统计
  • |
  • 参考文献
  • |
  • 相似文献
  • |
  • 引证文献
  • |
  • 文章评论
    摘要:

    第三纪孑遗植物新疆野苹果,是现代栽培苹果的祖先, 也是国家Ⅱ级重点保护野生植物。目前国内仅分布在新疆伊犁和塔城地区。近十几年来,其分布面积、种群和个体数量日益减少。为全面摸清新疆野苹果在国内整个分布区的生存现状、了解其群落物种组成、种群结构与动态特征,对分布在伊犁和塔城不同分布点的新疆野苹果天然种群进行了野外调查。应用"空间代替时间"理论编制新疆野苹果种群特定时间生命表,绘制种群存活曲线和死亡率曲线;利用生存分析理论,分析其种群数量动态变化;并应用时间序列模型,预测种群的发展趋势。结果表明:1)新疆野苹果主要生长在海拔870-1576 m的陡坡、沟谷、河漫滩和缓坡草场四种生境。河漫滩生境,物种丰富度和植被盖度最高,植被盖度高达70%-80%。该生境下新疆野苹果多与杏、黄果山楂、毛叶稠李、新疆忍冬等物种形成共优群落。其他三种生境,新疆野苹果多以纯林形式存在。2)伊犁种群病虫害严重,死亡率为7%,干枝、枯枝率达85%-90%;塔城种群几乎无病虫害,死亡率仅为2%,干枝、枯枝率仅为2%-5%。3)伊犁种群为衰退型,种群幼龄个体少,尤其是幼苗数量极少、种群多个生长发育阶段均呈现衰退的动态。严重的病虫害、过渡放牧和收割牧草是造成伊犁种群衰退的主要因素。塔城种群为增长型,种群幼龄个体多,幼苗数量足,但种群从幼苗过渡到幼树极困难。塔城不同分布点种群面临的问题不同。4)在未来2、3和4个龄级后,伊犁和塔城种群均呈现幼龄(幼树和小树)个体减少、老龄(大树和老树)个体增加的态势,种群衰退趋势明显。基于对新疆野苹果种群现状和存在问题的分析,结合实地调查,提出如下建议:1)针对伊犁种群,应首先应用生物防治等技术严格控制住病虫害的继续蔓延和加重;其次考虑建立国家级或省级新疆野苹果自然保护区并在保护区划分出优先最小保护单元,缓解一直存在的林牧矛盾。2)针对塔城种群,应根据不同分布点面临问题的不同制定相应的保护和管理措施。对幼苗死亡率高的额敏种群,应首先减少或限定风景区游客数量,其次在风景区内划分核心保护区和一般保护区,核心保护区内禁止人为活动;对托里种群,应首先加快建立高精度的自然灾害监测预警体系,其次减少放牧;对裕民种群,应采取人工辅助措施优化生境,促进种群幼苗的萌发、各阶段的顺利过渡和种群的稳定增长。

    Abstract:

    Malus sieversii (Ledeb.) M. Roem., a tertiary relict species, is the ancestor of modern cultivated apples. It is also a second-class key protected wild plant in China, only distributed in Ili and Tacheng Prefecture of Xinjiang in China. In the past decade, its distribution area, the number of populations and individuals has been decreasing. In order to comprehensively understand the survival status of M. sieversii in the whole distribution range of China, its community species composition, population structure and dynamic characteristics, a field investigation on the natural population of M. sieversii distributed in different sites of Ili and Tacheng was conducted. The "space instead of time" theory was used to compile a time-specific life table of M. sieversii, and its population survival curve and death curve were drawn. The survival analysis theory was used to analyze the dynamic changes of the population. Time series models were used to predict population trends. The results showed that: 1) M. sieversii mainly grew in four habitats (steep slope, valley, flood plain and gentle slope grassland) at an altitude of 870-1576 m. Among the four habitats, the flood plain had the highest species richness and vegetation coverage, reaching 70%-80%. In this habitat, M. sieversii coexisted with other species such as Armeniaca vulgaris, Crataegus pinnatifida, Lonicera tatarica and Spiraea salicifolia. while in other three habitats, M. sieversii mostly exists in pure forest. 2) The Ili population has serious pests and diseases, with a mortality rate of 7%, and a dry and dead branch rate of 85%-90%. The population of Tacheng is almost free of diseases and pests, with a mortality rate of only 2% and the dry and dead branch rate of only 2%-5%. 3) The population of Ili showed a declining pattern with few young individuals especially seedlings and a declinging trend dynamic multiple growth and development stages. Severe pests and diseases, overgrazing, and harvesting of forage are the main factors causing population decline. The population of Tacheng showed a growing pattern with sufficient young individuals especially seedlings. But there are huge difficulties in successfully transition from seedlings to young trees and young trees to small trees. The population in different sites in Tacheng faces different problems. 4) After the next 2nd, 3rd and 4th age classes, both Ili and Tacheng populations showed a trend of decreasing of young individuals and increasing of elderly trees, and the population declining trend was obvious. Based on the analyses of the current situation and existing problems of M. sieversii, combined with field investigations, the following suggestions are proposed: 1) For the Ili population, biological control and other technologies should be applied first to strictly control the continued spread and aggravation of diseases and pests; Secondly, the establishment of a national or provincial-level Nature Reserve of M. sieversii and the division of priority and minimum protection units in the reserve should be considered to alleviate the long-standing forest pastoral conflict. 2) For the Tacheng population, different protection and management measures should be made based on different problems faced by different populations. For Emin population with high seedling mortality rates, the number of tourists to scenic areas should be reduced or limited first. Secondly, core protected areas and general protected areas should be divided within the scenic areas, and human activities are strictly prohibited within the core protected areas; For Tuoli population, we should first accelerate the establishment of a high-precision monitoring and early warning system for natural disasters, and secondly reduce grazing; For Yumin population, artificial assistance measures should be taken to optimize the habitat, promote the germination of seedlings, smooth transition at each stage, and stable growth of the population.

    参考文献
    相似文献
    引证文献
引用本文

秦爱丽,刘博,陈强,郑祥坤,金崑.伊犁和塔城地区新疆野苹果种群结构及动态特征.生态学报,2025,45(1):197~209

复制
分享
文章指标
  • 点击次数:
  • 下载次数:
  • HTML阅读次数:
  • 引用次数: