Chin J Plant Ecol ›› 2025, Vol. 49 ›› Issue (3): 379-392.DOI: 10.17521/cjpe.2024.0035 cstr: 32100.14.cjpe.2024.0035
Special Issue: 生物多样性
• Research Articles • Previous Articles Next Articles
LI Dong-Mei, SUN Long, HAN Yu, HU Tong-Xin, YANG Guang, CAI Hui-Ying*()
Received:
2024-02-02
Accepted:
2024-06-14
Online:
2025-03-20
Published:
2024-06-17
Contact:
CAI Hui-Ying
Supported by:
LI Dong-Mei, SUN Long, HAN Yu, HU Tong-Xin, YANG Guang, CAI Hui-Ying. Impact of prescribed burning on biodiversity and ecosystem multifunctionality of Pinus koraiensis plantation[J]. Chin J Plant Ecol, 2025, 49(3): 379-392.
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URL: https://www.plant-ecology.com/EN/10.17521/cjpe.2024.0035
处理 Treatment | 海拔 Altitude (m) | 坡度 Slope (°) | 林龄 Forest age (a) | 平均树高 Mean tree height (m) | 平均胸径 Mean diameter at breast height (cm) |
---|---|---|---|---|---|
计划火烧样地 Prescribed burning plot | 215.0 | 19.0 | 59 | 10.5 | 26.5 |
对照样地 Control plot | 219.1 | 21.0 | 58 | 11.2 | 26.2 |
Table 1 Basic information of the study plot of prescribed burning experiment in Hongqi Forest, Hegang, Heilongjiang
处理 Treatment | 海拔 Altitude (m) | 坡度 Slope (°) | 林龄 Forest age (a) | 平均树高 Mean tree height (m) | 平均胸径 Mean diameter at breast height (cm) |
---|---|---|---|---|---|
计划火烧样地 Prescribed burning plot | 215.0 | 19.0 | 59 | 10.5 | 26.5 |
对照样地 Control plot | 219.1 | 21.0 | 58 | 11.2 | 26.2 |
Fig. 2 Structural equation model for the effects of understory plant diversity and soil microbial diversity on ecosystem multifunctionality after prescribed burning. Numbers in parentheses indicate the hypothetical path in Table 2. EMF, ecosystem multifunctionality.
路径序数 Pathway No. | 假设路径 Hypothesized pathway | 生态机制 Ecological mechanism |
---|---|---|
1 | 计划火烧→生态系统多功能性 Prescribed burning→ecosystem multifunctionality | 计划火烧影响森林生态系统的养分循环和能量流动, 改变林内生物的生存环境, 影响森林生态系统多功能性 Prescribed burning affects the nutrient cycling and energy flow in forest ecosystems, alters the within forest environment, and affects the multifunctionality of forest ecosystems |
2, 3, 5 | 计划火烧→数量性状、效率性状、功能/物种多样性 Prescribed burning→Traitquantity, Traitefficiency, functional/species diversity | 计划火烧改变植物的生存环境, 进而影响物种组成、功能多样性、植物数量性状和效率性状 Prescribed burning alters plant habitat, which in turn affects species composition, functional diversity, plant Traitquantity and Traitefficiency |
4 | 计划火烧→土壤微生物多样性 Prescribed burning→soil microbial diversity | 计划火烧改变土壤微生物群落的组成和结构, 影响土壤微生物多样性 Prescribed burning alters the composition and structure of soil microbial communities and affects soil microbial diversity |
6, 7, 8 | 数量性状、效率性状、功能/物种多样性→土壤微生物多样性 Traitquantity, Traitefficiency, functional/species diversity→soil microbial diversity | 植物属性(即数量性状、效率性状、功能多样性和物种多样性)可决定土壤微生物群落的多样性 Plant attributes (i.e., Traitquantity, Traitefficiency, functional diversity and species diversity) can affect the diversity of soil microbial communities |
9 | 数量性状→生态系统多功能性 Traitquantity→ecosystem multifunctionality | 单位土地面积的功能性状可以有效预测森林生态系统多功能性 Functional traits per unit area can be an effective predictor of forest ecosystem multifunctionality |
10 | 效率性状→生态系统多功能性 Traitefficiency→ecosystem multifunctionality | 根据选择效应, 群落加权功能性状可以促进森林生态系统多功能性 Community weighted functional traits can promote multifunctionality of forest ecosystems through selection effects |
11 | 土壤微生物多样性→生态系统多功能性 Soil microbial diversity→ecosystem multifunctionality | 土壤微生物多样性和土壤群落组成影响森林生态系统的多功能性 Soil microbial diversity and soil community composition affect the multifunctionality of forest ecosystems |
12 | 功能多样性/物种多样性→生态系统多功能性 Functional/species diversity→ecosystem multifunctionality | 植物功能多样性和物种多样性通过生态位互补效应促进森林生态系统多功能性 Plant functional diversity and species diversity promote multifunctionality of forest ecosystems through niche complementary effects |
Table 2 A brief description of the ecological mechanisms associated with hypothetical pathways in a structural equation conceptual model of the impact of biodiversity on ecosystem multifunctionality following prescribed burning
路径序数 Pathway No. | 假设路径 Hypothesized pathway | 生态机制 Ecological mechanism |
---|---|---|
1 | 计划火烧→生态系统多功能性 Prescribed burning→ecosystem multifunctionality | 计划火烧影响森林生态系统的养分循环和能量流动, 改变林内生物的生存环境, 影响森林生态系统多功能性 Prescribed burning affects the nutrient cycling and energy flow in forest ecosystems, alters the within forest environment, and affects the multifunctionality of forest ecosystems |
2, 3, 5 | 计划火烧→数量性状、效率性状、功能/物种多样性 Prescribed burning→Traitquantity, Traitefficiency, functional/species diversity | 计划火烧改变植物的生存环境, 进而影响物种组成、功能多样性、植物数量性状和效率性状 Prescribed burning alters plant habitat, which in turn affects species composition, functional diversity, plant Traitquantity and Traitefficiency |
4 | 计划火烧→土壤微生物多样性 Prescribed burning→soil microbial diversity | 计划火烧改变土壤微生物群落的组成和结构, 影响土壤微生物多样性 Prescribed burning alters the composition and structure of soil microbial communities and affects soil microbial diversity |
6, 7, 8 | 数量性状、效率性状、功能/物种多样性→土壤微生物多样性 Traitquantity, Traitefficiency, functional/species diversity→soil microbial diversity | 植物属性(即数量性状、效率性状、功能多样性和物种多样性)可决定土壤微生物群落的多样性 Plant attributes (i.e., Traitquantity, Traitefficiency, functional diversity and species diversity) can affect the diversity of soil microbial communities |
9 | 数量性状→生态系统多功能性 Traitquantity→ecosystem multifunctionality | 单位土地面积的功能性状可以有效预测森林生态系统多功能性 Functional traits per unit area can be an effective predictor of forest ecosystem multifunctionality |
10 | 效率性状→生态系统多功能性 Traitefficiency→ecosystem multifunctionality | 根据选择效应, 群落加权功能性状可以促进森林生态系统多功能性 Community weighted functional traits can promote multifunctionality of forest ecosystems through selection effects |
11 | 土壤微生物多样性→生态系统多功能性 Soil microbial diversity→ecosystem multifunctionality | 土壤微生物多样性和土壤群落组成影响森林生态系统的多功能性 Soil microbial diversity and soil community composition affect the multifunctionality of forest ecosystems |
12 | 功能多样性/物种多样性→生态系统多功能性 Functional/species diversity→ecosystem multifunctionality | 植物功能多样性和物种多样性通过生态位互补效应促进森林生态系统多功能性 Plant functional diversity and species diversity promote multifunctionality of forest ecosystems through niche complementary effects |
生态系统功能 Ecosystem function | 单位 Unit | 对照样地 Control plot | 计划火烧样地 Prescribed burning plot |
---|---|---|---|
生态系统多功能性 EMF | - | 0.55 ± 0.06b | 0.74 ± 0.11a |
林下植被生物量 Understory biomass | g∙m-2 | 12.05 ± 4.08b | 22.52 ± 8.15a |
凋落物生物量 Litter mass | g∙m-2 | 198.93 ± 30.91b | 271.38 ± 71.99a |
土壤碳储量 Soil carbon storage | g∙m-2 | 0.27 ± 0.04a | 0.32 ± 0.06a |
土壤铵态氮含量 Soil NH4+-N content | mg∙kg-1 | 16.85 ± 3.83a | 17.63 ± 3.46a |
土壤硝态氮含量 Soil NO3--N content | mg∙kg-1 | 2.50 ± 0.78b | 3.84 ± 0.61a |
Table 3 Changes of ecosystem functioning of Pinus koraiensis plantation after prescribed burning (mean ± SD)
生态系统功能 Ecosystem function | 单位 Unit | 对照样地 Control plot | 计划火烧样地 Prescribed burning plot |
---|---|---|---|
生态系统多功能性 EMF | - | 0.55 ± 0.06b | 0.74 ± 0.11a |
林下植被生物量 Understory biomass | g∙m-2 | 12.05 ± 4.08b | 22.52 ± 8.15a |
凋落物生物量 Litter mass | g∙m-2 | 198.93 ± 30.91b | 271.38 ± 71.99a |
土壤碳储量 Soil carbon storage | g∙m-2 | 0.27 ± 0.04a | 0.32 ± 0.06a |
土壤铵态氮含量 Soil NH4+-N content | mg∙kg-1 | 16.85 ± 3.83a | 17.63 ± 3.46a |
土壤硝态氮含量 Soil NO3--N content | mg∙kg-1 | 2.50 ± 0.78b | 3.84 ± 0.61a |
Fig. 3 Correlation between understory plant biodiversity (species diversity, functional diversity, Traitefficiency, Traitquantity) and ecosystem multifunctionality (EMF) in Pinus koraiensis plantation. CWM, community weighted mean; CWMLDMC, CWM of leaf dry matter content; CWMLeaf-N, CWM of leaf nitrogen content; CWMLeaf-P, CWM of leaf phosphorus content; CWMMH, CWM of maximum height; CWMSLA, CWM of specific leaf area; FDLDMC, FDis based on leaf dry matter content; FDLeaf-N, FDis based on leaf nitrogen content; FDLeaf-P, FDis based on leaf phosphorus content; FDMH, FDis based on maximum height; FDSLA, FDis based on specific leaf area; FDis, functional dispersion; FEve, functional evenness; FRic, functional richness; LAI, leaf area index; LMI, leaf mass index; LNI, total leaf nitrogen content per unit area; LPI, total leaf phosphorus content per unit area; S, species richness.
Fig. 4 Correlation between belowground biodiversity and ecosystem multifunctionality in Pinus koraiensis plantation. EMF, ecosystem multifunctionality.
Fig. 5 Structural equation model for the effects of prescribed burning, understory plant diversity (functional diversity, Traitefficiency, Traitquantity) and soil microbial diversity on ecosystem multifunctionality (EMF). Solid arrows represent significant pathways (p < 0.05) and dashed arrows represent non-significant pathways (p > 0.05). The figures on lines are standardized path coefficients (*, p < 0.05; **, p < 0.01; ***, p < 0.001). R2 value represents the proportion of variance explained for each response variable. CFI, comparative fit index; p, probability of significance value; RMSEA, root mean square error of approximation; SRMR, standardized root mean square residual. CWMLeaf-N, community weighted mean of leaf nitrogen content; FDLDMC, functional dispersion based on leaf dry matter content; LNI, total leaf nitrogen content per unit area.
Fig. 6 Direct and indirect effects (A) and relative contributions (B) of prescribed burning, understory plant diversity (functional diversity, Traitefficiency, Traitquantity) and soil microbial diversity to ecosystem multifunctionality. Dark colored bars indicate direct effects and light-colored bars indicate indirect effects in A. B are percentages of the absolute value of the sum of direct and indirect effects.
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