
生物多样性 ›› 2024, Vol. 32 ›› Issue (12): 24255. DOI: 10.17520/biods.2024255 cstr: 32101.14.biods.2024255
徐智超1,2(
), 朱美慧1,2, 毛子昆1,2(
), 王绪高1,2,*(
)(
)
收稿日期:2024-06-23
接受日期:2024-09-27
出版日期:2024-12-20
发布日期:2024-12-17
通讯作者:
E-mail: 基金资助:
Zhichao Xu1,2(
), Meihui Zhu1,2, Zikun Mao1,2(
), Xugao Wang1,2,*(
)(
)
Received:2024-06-23
Accepted:2024-09-27
Online:2024-12-20
Published:2024-12-17
Contact:
E-mail: Supported by:摘要: 大气氮沉降是驱动森林生物多样性变化的重要因子。尽管已有大量研究证实氮添加能够显著改变森林生态系统林下层种群密度以及物种多样性, 但现有研究大多局限于草本植物。而乔木幼苗阶段作为森林更新的关键时期, 其物种组成及动态变化对氮添加的响应趋势和内在机理仍不清晰。本研究依托长白山温带阔叶红松林氮添加控制试验平台, 基于连续7年的乔木幼苗动态监测数据, 分析不同氮添加处理对幼苗数量动态及物种多样性的影响; 并以负密度制约效应为切入点, 探讨氮添加影响物种多样性的机制。结果表明, 氮添加显著降低了群落水平的幼苗总个体和增补数量, 但增强了幼苗年际动态相似性。低氮处理的物种丰富度和Shannon-Wiener指数均显著低于对照组, 而Shannon-Wiener指数在中氮处理下显著高于对照组。此外, 同种幼苗负密度制约效应随氮添加浓度的升高呈现加剧趋势, 且与物种丰富度、Shannon-Wiener指数和Pielou均匀度指数显著负相关, 这证明了氮沉降对同种负密度制约效应的影响是改变物种多样性的潜在机制。综上, 本研究明确了氮添加对长白山温带阔叶红松林乔木幼苗动态的影响, 以密度制约效应为视角揭示了氮添加对物种多样性的作用机理, 为研究氮沉降背景下温带森林幼苗动态及其响应机制提供了新思路。
徐智超, 朱美慧, 毛子昆, 王绪高 (2024) 氮添加对东北温带阔叶红松林幼苗动态的影响. 生物多样性, 32, 24255. DOI: 10.17520/biods.2024255.
Zhichao Xu, Meihui Zhu, Zikun Mao, Xugao Wang (2024) Effects of nitrogen addition on seedling dynamics in a broad-leaved Korean pine forest in Northeast China. Biodiversity Science, 32, 24255. DOI: 10.17520/biods.2024255.
图1 对照和加氮处理下幼苗动态及其多样性指数(平均值 ± 标准误)。CK、LN、MN和HN分别代表对照、低氮、中氮和高氮处理。图中不同小写字母表示幼苗动态在不同处理间差异显著(P < 0.05)。
Fig. 1 Effects of nitrogen addition on seedling dynamics (mean ± SE). CK, LN, MN, and HN represent the contrast, low-level nitrogen addition, medium-level nitrogen addition, and high-level nitrogen addition, respectively. The different lowercase letters indicate significant difference (P < 0.05).
图2 加氮处理对同种和异种密度制约效应的影响。CK、LN、MN和HN分别代表对照、低氮、中氮和高氮处理。
Fig. 2 Effects of nitrogen addition on conspecific and heterospecific density dependence. CK, LN, MN, and HN represent the control, low-level nitrogen addition, medium-level nitrogen addition, and high-level nitrogen addition, respectively. A.con, Conspecific adult density dependence; A.het, Heterospecific adult density dependence; S.con, Conspecific seedling density dependence; S.het, Heterospecific seedling density dependence.
图3 加氮处理调节邻域幼苗和大树密度对幼苗存活的影响。CK、LN、MN和HN分别代表对照、低氮、中氮和高氮处理。
Fig. 3 Response of seedling survival to seedling/adult density for nitrogen addition. CK, LN, MN, and HN represent the control, low-level nitrogen addition, medium-level nitrogen addition, and high-level nitrogen addition, respectively.
图4 同种和异种密度制约效应与幼苗多样性的关系。实线代表幼苗多样性随密度制约效应显著变化(P < 0.05), 虚线代表幼苗多样性随密度制约效应变化不显著(P > 0.05)。S.con: 同种幼苗密度制约效应; A.con: 同种大树密度制约效应; S.het: 异种幼苗密度制约效应; A.het: 异种大树密度制约效应。
Fig. 4 The relationships between conspecific/heterospecific density dependence and seedling diversity. Solid lines indicate the seedling diversity changed significantly with seedling/adult density dependence (P < 0.05), and dashed lines represent insignificant changes in seedling diversity in response to seedling/adult density dependence (P > 0.05). S.con, Conspecific seedling density dependence, A.con, Conspecific adult density dependence; S.het, Heterospecific seedling density dependence; A.het, Heterospecific adult density dependence.
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