{"title":"青藏高原东南部健康亚高山针叶树与衰败亚高山针叶树的径向生长和气候反应","authors":"Lingzhuo Luo , Wenzhi Wang , Zhehong Wu , Yong Su","doi":"10.1016/j.ecolind.2024.112845","DOIUrl":null,"url":null,"abstract":"<div><div>The forest loss and degradation caused by tree heart rot presents an increasingly challenging issue for the protection and utilization of forest resources. Yet, it is questionable whether heartwood-decayed trees can still function on par with healthy trees. Here, using tree ring data, we established basal area increment (BAI) series of healthy and heartwood-decayed fir trees at four sites (<em>Abies spectabilis</em> in Bomi; <em>A. georgei</em> Orr in Deqin as well as the Sygera Mountain; <em>A. fabri</em> Craib in Yajiageng) in the southeastern Qinghai-Tibetan Plateau (QTP). We conducted a comparative analysis of the difference in the BAI, response to climate factors and elasticity under environmental stress between the healthy and decayed fir. The results show that, in QTP, fir susceptibility to decay is uncorrelated with growth rates. However, after decaying occurs in fir trees, their radial growth is restricted in warm and humid areas (i.e., at Bomi and Yajiageng). The average BAI of healthy fir is 70.32 % and 86.32 % higher than that of decayed fir in Bomi and Yajiageng respectively (p < 0.01), but no significant difference in Deqin and Sygera (p > 0.05). Moreover, healthy fir exhibits a more pronounced response to climatic conditions. Almost all BAI series of healthy and decayed fir in the southeastern QTP is positively correlated with the temperature and vapor pressure deficit. Under temperature stress, decayed fir trees are less resistant at three sites. This empirical study supports that there is no correlation between conifer trees’ radial growth rate and their likelihood of heartwood decay, and provides a compelling explanation for the constrained growth of decayed fir trees. Our findings can bolster the accurate assessment of carbon sinks and the conservation of forest resources in regions prone to high-decaying risks.</div></div>","PeriodicalId":11459,"journal":{"name":"Ecological Indicators","volume":"169 ","pages":"Article 112845"},"PeriodicalIF":7.0000,"publicationDate":"2024-11-15","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Radial growth and climate responses of healthy versus decayed subalpine conifer trees in the southeastern Qinghai-Tibetan Plateau\",\"authors\":\"Lingzhuo Luo , Wenzhi Wang , Zhehong Wu , Yong Su\",\"doi\":\"10.1016/j.ecolind.2024.112845\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<div><div>The forest loss and degradation caused by tree heart rot presents an increasingly challenging issue for the protection and utilization of forest resources. Yet, it is questionable whether heartwood-decayed trees can still function on par with healthy trees. Here, using tree ring data, we established basal area increment (BAI) series of healthy and heartwood-decayed fir trees at four sites (<em>Abies spectabilis</em> in Bomi; <em>A. georgei</em> Orr in Deqin as well as the Sygera Mountain; <em>A. fabri</em> Craib in Yajiageng) in the southeastern Qinghai-Tibetan Plateau (QTP). We conducted a comparative analysis of the difference in the BAI, response to climate factors and elasticity under environmental stress between the healthy and decayed fir. The results show that, in QTP, fir susceptibility to decay is uncorrelated with growth rates. However, after decaying occurs in fir trees, their radial growth is restricted in warm and humid areas (i.e., at Bomi and Yajiageng). The average BAI of healthy fir is 70.32 % and 86.32 % higher than that of decayed fir in Bomi and Yajiageng respectively (p < 0.01), but no significant difference in Deqin and Sygera (p > 0.05). Moreover, healthy fir exhibits a more pronounced response to climatic conditions. Almost all BAI series of healthy and decayed fir in the southeastern QTP is positively correlated with the temperature and vapor pressure deficit. Under temperature stress, decayed fir trees are less resistant at three sites. This empirical study supports that there is no correlation between conifer trees’ radial growth rate and their likelihood of heartwood decay, and provides a compelling explanation for the constrained growth of decayed fir trees. 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引用次数: 0
摘要
树木心材腐烂造成的森林损失和退化对森林资源的保护和利用提出了日益严峻的挑战。然而,心材腐烂的树木是否仍能发挥与健康树木同等的功能还是个问题。在此,我们利用树环数据,在青藏高原东南部的四个地点(波密的Abies spectabilis、德钦和色季拉山的A. georgei Orr、雅家岗的A. fabri Craib)建立了健康杉木和心材腐烂杉木的基部面积增量(BAI)序列。我们对健康冷杉和腐烂冷杉在 BAI、对气候因子的响应和环境压力下的弹性方面的差异进行了比较分析。结果表明,在青藏高原,冷杉易腐性与生长率无关。然而,冷杉发生腐烂后,其径向生长在温暖潮湿地区(即波密和雅家坑)受到限制。在波密和雅家坑,健康冷杉的平均 BAI 分别比腐烂冷杉高 70.32 % 和 86.32 %(p <0.01),但在德钦和赛格拉没有显著差异(p >0.05)。此外,健康冷杉对气候条件的反应更为明显。QTP东南部健康冷杉和腐烂冷杉的几乎所有 BAI 序列都与温度和蒸气压差呈正相关。在温度胁迫下,三个地点的衰落杉树的抵抗力较弱。这项实证研究证明,针叶树的径向生长速度与其心材腐烂的可能性之间不存在相关性,并为腐烂杉树的生长受限提供了令人信服的解释。我们的研究结果有助于对碳汇进行准确评估,并保护高腐烂风险地区的森林资源。
Radial growth and climate responses of healthy versus decayed subalpine conifer trees in the southeastern Qinghai-Tibetan Plateau
The forest loss and degradation caused by tree heart rot presents an increasingly challenging issue for the protection and utilization of forest resources. Yet, it is questionable whether heartwood-decayed trees can still function on par with healthy trees. Here, using tree ring data, we established basal area increment (BAI) series of healthy and heartwood-decayed fir trees at four sites (Abies spectabilis in Bomi; A. georgei Orr in Deqin as well as the Sygera Mountain; A. fabri Craib in Yajiageng) in the southeastern Qinghai-Tibetan Plateau (QTP). We conducted a comparative analysis of the difference in the BAI, response to climate factors and elasticity under environmental stress between the healthy and decayed fir. The results show that, in QTP, fir susceptibility to decay is uncorrelated with growth rates. However, after decaying occurs in fir trees, their radial growth is restricted in warm and humid areas (i.e., at Bomi and Yajiageng). The average BAI of healthy fir is 70.32 % and 86.32 % higher than that of decayed fir in Bomi and Yajiageng respectively (p < 0.01), but no significant difference in Deqin and Sygera (p > 0.05). Moreover, healthy fir exhibits a more pronounced response to climatic conditions. Almost all BAI series of healthy and decayed fir in the southeastern QTP is positively correlated with the temperature and vapor pressure deficit. Under temperature stress, decayed fir trees are less resistant at three sites. This empirical study supports that there is no correlation between conifer trees’ radial growth rate and their likelihood of heartwood decay, and provides a compelling explanation for the constrained growth of decayed fir trees. Our findings can bolster the accurate assessment of carbon sinks and the conservation of forest resources in regions prone to high-decaying risks.
期刊介绍:
The ultimate aim of Ecological Indicators is to integrate the monitoring and assessment of ecological and environmental indicators with management practices. The journal provides a forum for the discussion of the applied scientific development and review of traditional indicator approaches as well as for theoretical, modelling and quantitative applications such as index development. Research into the following areas will be published.
• All aspects of ecological and environmental indicators and indices.
• New indicators, and new approaches and methods for indicator development, testing and use.
• Development and modelling of indices, e.g. application of indicator suites across multiple scales and resources.
• Analysis and research of resource, system- and scale-specific indicators.
• Methods for integration of social and other valuation metrics for the production of scientifically rigorous and politically-relevant assessments using indicator-based monitoring and assessment programs.
• How research indicators can be transformed into direct application for management purposes.
• Broader assessment objectives and methods, e.g. biodiversity, biological integrity, and sustainability, through the use of indicators.
• Resource-specific indicators such as landscape, agroecosystems, forests, wetlands, etc.