植物生态学报 ›› 2023, Vol. 47 ›› Issue (7): 922-931.DOI: 10.17521/cjpe.2022.0105 cstr: 32100.14.cjpe.2022.0105
所属专题: 全球变化与生态系统; 生态化学计量; 青藏高原植物生态学:生态系统生态学; 生物地球化学; 草原与草业
收稿日期:2022-03-25
接受日期:2022-07-15
出版日期:2023-07-20
发布日期:2023-07-21
作者简介:ORCID: 张法伟: 0000-0003-0693-7956
基金资助:
LI Hong-Qin1,2,3, ZHANG Fa-Wei2,3,4,*(
), YI Lü-Bei5
Received:2022-03-25
Accepted:2022-07-15
Online:2023-07-20
Published:2023-07-21
Supported by:摘要:
降水格局改变和氮沉降增加是草地生态系统结构及功能演变的重要影响因素, 其对高寒草甸土壤和植物的化学计量的影响存在很大变异, 限制了对高寒草甸生态功能预测的准确性。该研究基于祁连山东段南麓高寒草甸降水改变(减雨50%和增雨50%)和氮添加(10 g·m-2·a-1)的控制实验平台, 分析了2017-2020年表层(0-10 cm)土壤有机碳、全氮、全磷含量和优势植物麻花艽(Gentiana straminea)、垂穗披碱草(Elymus nutans)、黄花棘豆(Oxytropis ochrocephala)和矮生嵩草(Kobresia humilis)的叶片碳(LC)、氮(LN)、磷(LP)和钾(LK)含量等变化, 以明晰土壤和植物的化学计量特征对降水改变和氮添加的响应。结果表明, 土壤化学计量特征的变异存在显著年际效应, 与实验处理无显著关系。地上活体生物量(PB)存在显著的年际差异, 并受到氮添加的显著影响。优势物种叶片化学计量特征的变异因物种而异。垂穗披碱草叶片化学计量特征的变化均不显著, 属于资源保守型物种, 而矮生嵩草的变化显著, 敏感性较强。基于处理样地与对照样地每年指标相对变化(Δ)的分析表明, 氮添加显著提高了ΔPB达15.6%。降水减少显著降低了黄花棘豆ΔLC达6.8%, 增加了矮生嵩草ΔLP达19.8%。研究表明仅氮添加提高了PB, 降水减少改变了部分物种LC和LP含量, 土壤和植物叶片的化学计量特征变异的年际效应或物种效应大于实验处理效应, 凸显了高寒草甸生态系统对降水改变和氮添加响应的复杂性。
李红琴, 张法伟, 仪律北. 高寒草甸表层土壤和优势植物叶片的化学计量特征对降水改变和氮添加的响应. 植物生态学报, 2023, 47(7): 922-931. DOI: 10.17521/cjpe.2022.0105
LI Hong-Qin, ZHANG Fa-Wei, YI Lü-Bei. Stoichiometric responses in topsoil and leaf of dominant species to precipitation change and nitrogen addition in an alpine meadow. Chinese Journal of Plant Ecology, 2023, 47(7): 922-931. DOI: 10.17521/cjpe.2022.0105
图1 海北高寒草甸实验小区布置示意图。+50%, 降水增加50%; -50%, 降水减少50%; CK, 对照; E, 微生物肥添加; K, 钾添加; N, 氮添加; N+50%, 氮添加及降水增加50%; N-50%, 氮添加及降水减少50%; NK, 氮钾添加; NP, 氮磷添加; NPK, 氮磷钾添加; NPK+50%, 氮磷钾添加及降水增加50%; NPK-50%, 氮磷钾添加及降水减少50%; NPK+E, 氮磷钾+微生物肥添加; P, 磷添加; PK, 磷钾添加。
Fig. 1 Layout of experiment plots of the alpine meadow in Haibei Station. +50%, rainfall enrichment by 50%; -50%, rainfall reduction by 50%; CK, control check; E, microorganism addition; K, potassium addition; N, nitrogen addition; N+50%, N and rainfall enrichment by 50%; N-50%, N and rainfall reduction by 50%; NK, N and K; NP, N and phosphorus addition; NPK, N, P, and K; NPK+50%, N, P, and K and rainfall enrichment by 50%; NPK-50%, N, P, K and rainfall reduction by 50%; NPK+E, N, P, K and microorganism addition; PK, P and K.
| 处理 Treatment | SOC | SN | SP | SOC:SN | SOC:SP | SN:SP | PB |
|---|---|---|---|---|---|---|---|
| 年份 Year | <0.001 | <0.001 | <0.001 | <0.001 | <0.001 | <0.001 | <0.001 |
| 降水改变 Rain | 0.24 | 0.23 | 0.67 | 0.85 | 0.76 | 0.79 | 0.23 |
| 氮添加 N | 0.59 | 0.69 | 0.50 | 0.40 | 0.76 | 0.88 | 0.01 |
| 年份×降水改变 Year × Rain | 0.08 | 0.35 | 0.72 | 0.08 | 0.32 | 0.74 | 0.99 |
| 年份×氮添加 Year × N | 0.85 | 0.62 | 0.74 | 0.78 | 0.86 | 0.90 | 0.02 |
| 降水改变×氮添加 Rain × N | 0.04 | 0.19 | 0.18 | 0.42 | 0.97 | 0.98 | 0.54 |
表1 降水改变和氮添加对海北高寒草甸土壤化学计量特征及植被地上活体生物量的混合效应模型
Table 1 Linear mixed-effect models of soil stoichiometry and aboveground plant biomass (PB) to precipitation change (Rain) and nitrogen addition (N) in an alpine meadow of Haibei Station
| 处理 Treatment | SOC | SN | SP | SOC:SN | SOC:SP | SN:SP | PB |
|---|---|---|---|---|---|---|---|
| 年份 Year | <0.001 | <0.001 | <0.001 | <0.001 | <0.001 | <0.001 | <0.001 |
| 降水改变 Rain | 0.24 | 0.23 | 0.67 | 0.85 | 0.76 | 0.79 | 0.23 |
| 氮添加 N | 0.59 | 0.69 | 0.50 | 0.40 | 0.76 | 0.88 | 0.01 |
| 年份×降水改变 Year × Rain | 0.08 | 0.35 | 0.72 | 0.08 | 0.32 | 0.74 | 0.99 |
| 年份×氮添加 Year × N | 0.85 | 0.62 | 0.74 | 0.78 | 0.86 | 0.90 | 0.02 |
| 降水改变×氮添加 Rain × N | 0.04 | 0.19 | 0.18 | 0.42 | 0.97 | 0.98 | 0.54 |
图2 海北高寒草甸表层土壤有机碳(A)、全氮(B)、全磷(C)含量和植被地上活体生物量(D)的年际差异(平均值±标准差)。不同小写字母表示差异显著(p < 0.05); 箱式图中的实心方块和横线分别为平均值和中位数。
Fig. 2 Interannual differences of topsoil organic carbon content (SOC, A), total nitrogen content (SN, B), total phosphorus content (SP, C), and aboveground plant biomass (PB, D) of the alpine meadow in Haibei Station (mean ± SD). Different lowercase letters represent significant difference (p < 0.05); solid squares and lines of boxes are mean and median values, respectively.
图3 海北高寒草甸植被地上活体生物量(A)、黄花棘豆叶片碳含量(B)、矮生嵩草叶片磷(C)及碳(D)含量的相对变化对降水改变和氮添加的响应(平均值±标准差)。不同小写字母表示差异显著(p < 0.05); 箱式图中的实心方块和横线分别为平均值和中位数。+50%, 降水增加50%; -50%, 降水减少50%; CK, 对照; N, 氮添加; N+50%, 氮添加及降水增加50%; N-50%, 氮添加及降水减少50%; Rain, 降水改变。
Fig. 3 Response of relative changes of aboveground plant biomass (ΔPB, A), leaf carbon content (ΔLC) of Oxytropis ochrocephala (B), leaf phosphorus content (ΔLP, C) and ΔLC (D) of Kobresia humilis to precipitation change (Rain) and nitrogen addition (N) of the alpine meadow in Haibei Station (mean ± SD). Different lowercase letters represent significant difference (p < 0.05); solid squares and lines of boxes are mean and median values, respectively. +50%, rainfall enrichment by 50%; -50%, rainfall reduction by 50%; CK, control check; N+50%, N addition and rainfall enrichment by 50%; N-50%, N addition and rainfall reduction by 50%.
图4 海北高寒草甸麻花艽、垂穗披碱草、黄花棘豆和矮生嵩草的叶片碳(A)、氮(B)、磷(C)和钾(D)含量的差异(平均值±标准差)。不同小写字母表示差异显著(p < 0.05); 箱式图中的实心方块和横线分别为平均值和中位数。
Fig. 4 Differences of leaf carbon content (LC, A), nitrogen content (LN, B), phosphorus content (LP, C), and potassium content (LK, D) of Gentiana straminea, Elymus nutans, Oxytropis ochrocephala, and Kobresia humilis of the alpine meadow in Haibei Station (mean ± SD). Different lowercase letters represent significant difference (p < 0.05); solid squares and line of boxes are mean and median values, respectively.
| 物种 Species | 化学计量 Stoichiometry | 年份 Year | Rain | N | 年份×降水改变 Year × Rain | 年份×氮添加 Year × N | Rain × N |
|---|---|---|---|---|---|---|---|
| 麻花艽 Gentiana straminea | LC | 0.18 | 0.52 | 0.79 | 0.43 | 0.47 | 0.94 |
| LN | 0.02 | 0.59 | 0.97 | 0.77 | 0.08 | 0.87 | |
| LP | 0.02 | 0.79 | 0.33 | 0.41 | 0.40 | 0.18 | |
| LK | 0.44 | 0.27 | 0.69 | 0.29 | 0.92 | 0.95 | |
| 垂穗披碱草 Elymus nutans | LC | 0.68 | 0.42 | 0.71 | 0.23 | 0.49 | 0.27 |
| LN | 0.31 | 0.06 | 0.26 | 0.59 | 0.42 | 0.26 | |
| LP | 0.65 | 0.69 | 0.56 | 0.90 | 0.83 | 0.89 | |
| LK | 0.45 | 0.67 | 0.19 | 0.79 | 0.64 | 0.68 | |
| 黄花棘豆 Oxytropis ochrocephala | LC | 0.03 | 0.03 | 0.97 | 0.03 | 0.82 | 0.70 |
| LN | 0.36 | 0.78 | 0.21 | 0.79 | 0.44 | 0.73 | |
| LP | 0.13 | 0.99 | 0.29 | 0.71 | 0.62 | 0.96 | |
| LK | 0.06 | 0.51 | 0.54 | 0.73 | 0.68 | 0.40 | |
| 矮生嵩草 Kobresia humilis | LC | 0.02 | 0.05 | 0.61 | 0.01 | 0.23 | 0.38 |
| LN | 0.03 | 0.64 | 0.23 | 0.48 | 0.38 | 0.16 | |
| LP | <0.001 | 0.02 | 0.62 | 0.34 | 0.53 | 0.53 | |
| LK | <0.001 | 0.16 | 0.21 | 0.53 | 0.72 | 0.47 |
表2 降水改变(Rain)和氮添加(N)对优势植物叶片碳(LC)、氮(LN)、磷(LP)和钾(LK)含量的混合效应模型
Table 2 Linear mixed-effect models of leaf carbon (LC), nitrogen (LN), phosphor (LP), and potassium (LK) of dominant plant species to precipitation change (P) and nitrogen addition (N)
| 物种 Species | 化学计量 Stoichiometry | 年份 Year | Rain | N | 年份×降水改变 Year × Rain | 年份×氮添加 Year × N | Rain × N |
|---|---|---|---|---|---|---|---|
| 麻花艽 Gentiana straminea | LC | 0.18 | 0.52 | 0.79 | 0.43 | 0.47 | 0.94 |
| LN | 0.02 | 0.59 | 0.97 | 0.77 | 0.08 | 0.87 | |
| LP | 0.02 | 0.79 | 0.33 | 0.41 | 0.40 | 0.18 | |
| LK | 0.44 | 0.27 | 0.69 | 0.29 | 0.92 | 0.95 | |
| 垂穗披碱草 Elymus nutans | LC | 0.68 | 0.42 | 0.71 | 0.23 | 0.49 | 0.27 |
| LN | 0.31 | 0.06 | 0.26 | 0.59 | 0.42 | 0.26 | |
| LP | 0.65 | 0.69 | 0.56 | 0.90 | 0.83 | 0.89 | |
| LK | 0.45 | 0.67 | 0.19 | 0.79 | 0.64 | 0.68 | |
| 黄花棘豆 Oxytropis ochrocephala | LC | 0.03 | 0.03 | 0.97 | 0.03 | 0.82 | 0.70 |
| LN | 0.36 | 0.78 | 0.21 | 0.79 | 0.44 | 0.73 | |
| LP | 0.13 | 0.99 | 0.29 | 0.71 | 0.62 | 0.96 | |
| LK | 0.06 | 0.51 | 0.54 | 0.73 | 0.68 | 0.40 | |
| 矮生嵩草 Kobresia humilis | LC | 0.02 | 0.05 | 0.61 | 0.01 | 0.23 | 0.38 |
| LN | 0.03 | 0.64 | 0.23 | 0.48 | 0.38 | 0.16 | |
| LP | <0.001 | 0.02 | 0.62 | 0.34 | 0.53 | 0.53 | |
| LK | <0.001 | 0.16 | 0.21 | 0.53 | 0.72 | 0.47 |
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