植物生态学报 ›› 2023, Vol. 47 ›› Issue (5): 644-659.DOI: 10.17521/cjpe.2022.0160 cstr: 32100.14.cjpe.2022.0160
李小玲1,2, 朱道明3, 余玉蓉1, 吴浩1, 牟利1, 洪柳1, 刘雪飞1, 卜贵军1, 薛丹4, 吴林1,*(
)
接受日期:2022-09-28
出版日期:2023-05-20
发布日期:2023-02-28
基金资助:
LI Xiao-Ling1,2, ZHU Dao-Ming3, YU Yu-Rong1, WU Hao1, MOU Li1, HONG Liu1, LIU Xue- Fei1, BU Gui-Jun1, XUE Dan4, WU Lin1,*(
)
Accepted:2022-09-28
Online:2023-05-20
Published:2023-02-28
Supported by:摘要:
以泥炭藓属(Sphagnum)植物为优势种的贫营养泥炭地是陆地生态系统重要的碳汇, 其优势植物的生长与分解动态关系着贫营养泥炭地碳汇潜力, 但有关氮沉降对贫营养泥炭地优势藓类植物生长与分解的影响还存在很大争议, 并且氮沉降对亚热带贫营养泥炭地优势藓类植物生长与分解的研究鲜有报道。该研究以鄂西南贫营养泥炭地为研究对象, 通过原位喷洒不同浓度的NH4Cl溶液, 采用生物量收割法和分解袋法, 探讨模拟氮沉降对泥炭藓(S. palustre)与金发藓(Polytrichum commune)生长及分解的影响。研究结果表明: (1)氮沉降对两种藓类植物生长高度与生物量均有明显的影响, 且两种藓类植物生长存在一定的氮沉降阈值, 约为3 g·m-2·a-1; (2)氮沉降对两种藓类植物生长影响程度不同, 金发藓对氮沉降的响应灵敏度要大于泥炭藓; (3)高浓度氮沉降(6和12 g·m-2·a-1)抑制了泥炭藓分解, 低浓度氮沉降(3 g·m-2·a-1)对泥炭藓分解的影响取决于分解时间, 而所有浓度氮沉降均抑制了金发藓凋落物的分解; (4)分解1年以后, 泥炭藓的最终质量残留率平均值为105.99%, 金发藓的最终质量残留率平均值为70.79%, 金发藓的分解速率远大于泥炭藓; (5)氮沉降对两种藓类凋落物化学元素含量与化学计量比有显著影响, 且与分解时间密切相关。
李小玲, 朱道明, 余玉蓉, 吴浩, 牟利, 洪柳, 刘雪飞, 卜贵军, 薛丹, 吴林. 模拟氮沉降对鄂西南贫营养泥炭地两种藓类植物生长与分解的影响. 植物生态学报, 2023, 47(5): 644-659. DOI: 10.17521/cjpe.2022.0160
LI Xiao-Ling, ZHU Dao-Ming, YU Yu-Rong, WU Hao, MOU Li, HONG Liu, LIU Xue- Fei, BU Gui-Jun, XUE Dan, WU Lin. Effects of simulated nitrogen deposition on growth and decomposition of two bryophytes in ombrotrophic peatland, southwestern Hubei, China. Chinese Journal of Plant Ecology, 2023, 47(5): 644-659. DOI: 10.17521/cjpe.2022.0160
| 物种 Species | 重要值 IV (%) | 物种 Species | 重要值 IV (%) |
|---|---|---|---|
| 泥炭藓 Sphagnum palustre* | 90.23 | 耳叶杜鹃 Rhododendron auriculatum | 24.94 |
| 大理薹草 Carex rubrobrunnea var. taliensis | 62.31 | 芒 Miscanthus sinensis | 23.45 |
| 齿缘吊钟花 Enkianthus serrulatus | 61.83 | 茶荚蒾 Viburnum setigerum | 13.26 |
| 多齿长尾槭 Acer caudatum var. multiserratum | 48.00 | 紫萁 Osmunda japonica | 11.64 |
| 金发藓 Polytrichum commune* | 40.35 | 华西华楸 Sorbus wilsoniana | 9.18 |
| 西南凤尾蕨 Pteris wallichiana | 36.25 | 湖北海棠 Malus hupehensis | 8.43 |
| 灯心草 Juncus effusus | 31.36 | 四川冬青 Ilex szechwanensis | 6.19 |
| 小灯心草 Juncus bufonius | 25.12 | 金丝桃 Hypericum monogynum | 4.81 |
表1 太山庙泥炭地主要物种重要值
Table 1 Important values of dominant plant species in Taishanmiao peatland
| 物种 Species | 重要值 IV (%) | 物种 Species | 重要值 IV (%) |
|---|---|---|---|
| 泥炭藓 Sphagnum palustre* | 90.23 | 耳叶杜鹃 Rhododendron auriculatum | 24.94 |
| 大理薹草 Carex rubrobrunnea var. taliensis | 62.31 | 芒 Miscanthus sinensis | 23.45 |
| 齿缘吊钟花 Enkianthus serrulatus | 61.83 | 茶荚蒾 Viburnum setigerum | 13.26 |
| 多齿长尾槭 Acer caudatum var. multiserratum | 48.00 | 紫萁 Osmunda japonica | 11.64 |
| 金发藓 Polytrichum commune* | 40.35 | 华西华楸 Sorbus wilsoniana | 9.18 |
| 西南凤尾蕨 Pteris wallichiana | 36.25 | 湖北海棠 Malus hupehensis | 8.43 |
| 灯心草 Juncus effusus | 31.36 | 四川冬青 Ilex szechwanensis | 6.19 |
| 小灯心草 Juncus bufonius | 25.12 | 金丝桃 Hypericum monogynum | 4.81 |
| 物种 Species | 初始总碳(C)含量 Initial total carbon (C) content (%) | 初始总氮(N)含量 Initial total nitrogen (N) content (%) | 初始总酚含量 Initial total phenolics content (%) | 初始C:N Initial C:N | 初始总酚:C Initial total phenolics:C | 初始总酚:N Initial total phenolics:N | 初始灰分含量 Initial ash content (%) |
|---|---|---|---|---|---|---|---|
| 泥炭藓 Sphagnum palustre | 37.39 ± 0.07b | 0.98 ± 0.03b | 1.26 ± 0.02b | 39.50 ± 0.09a | 3.34 ± 0.04b | 1.29 ± 0.02b | 0.96 ± 0.02b |
| 金发藓 Polytrichum commune | 42.28 ± 0.09a | 1.35 ± 0.01a | 2.04 ± 0.03a | 31.40 ± 0.22b | 4.83 ± 0.06a | 1.52 ± 0.01a | 4.17 ± 0.04a |
表2 太山庙泥炭地中泥炭藓和金发藓的初始化学组分(平均值±标准误, n = 4)
Table 2 Initial chemical composition of Sphagnum palustre and Polytrichum commune in Taishanmiao peatland (mean ± SE, n = 4)
| 物种 Species | 初始总碳(C)含量 Initial total carbon (C) content (%) | 初始总氮(N)含量 Initial total nitrogen (N) content (%) | 初始总酚含量 Initial total phenolics content (%) | 初始C:N Initial C:N | 初始总酚:C Initial total phenolics:C | 初始总酚:N Initial total phenolics:N | 初始灰分含量 Initial ash content (%) |
|---|---|---|---|---|---|---|---|
| 泥炭藓 Sphagnum palustre | 37.39 ± 0.07b | 0.98 ± 0.03b | 1.26 ± 0.02b | 39.50 ± 0.09a | 3.34 ± 0.04b | 1.29 ± 0.02b | 0.96 ± 0.02b |
| 金发藓 Polytrichum commune | 42.28 ± 0.09a | 1.35 ± 0.01a | 2.04 ± 0.03a | 31.40 ± 0.22b | 4.83 ± 0.06a | 1.52 ± 0.01a | 4.17 ± 0.04a |
| 因素 Factor | df | 高度增长量 Height increment (cm) | 净初级生产力 Net primary productivity (g·m-2) | ||
|---|---|---|---|---|---|
| F | p | F | p | ||
| 氮沉降 Nitrogen deposition | 3 | 5.210 | 0.007 | 30.851 | <0.001 |
| 物种 Species | 1 | 129.062 | <0.001 | 41.170 | 0.021 |
| 氮沉降×物种 Nitrogen deposition × species | 3 | 1.231 | 0.320 | 4.502 | 0.102 |
表3 氮沉降、物种及两者交互作用对两种苔藓高度增长量及净初级生产力影响的双因素方差分析
Table 3 Two-way ANOVA on the effects of nitrogen deposition, species and interaction on height increment, net primary productivity of two bryophytes
| 因素 Factor | df | 高度增长量 Height increment (cm) | 净初级生产力 Net primary productivity (g·m-2) | ||
|---|---|---|---|---|---|
| F | p | F | p | ||
| 氮沉降 Nitrogen deposition | 3 | 5.210 | 0.007 | 30.851 | <0.001 |
| 物种 Species | 1 | 129.062 | <0.001 | 41.170 | 0.021 |
| 氮沉降×物种 Nitrogen deposition × species | 3 | 1.231 | 0.320 | 4.502 | 0.102 |
图2 模拟氮沉降对生长季泥炭藓和金发藓高度增长量(A)及净初级生产力(B)的影响(平均值±标准误, n = 4)。不同小写字母表示泥炭藓在不同氮浓度间差异显著(p < 0.05), 不同大写字母表示金发藓在不同氮浓度间差异显著(p < 0.05)。*表示不同物种间差异显著(p < 0.05)。
Fig. 2 Effects of simulated nitrogen deposition on increment of height growth (A) and net primary productivity (B) of Sphagnum palustre and Polytrichum commune in the growing season (mean ± SE, n = 4). Different lowercase letters indicate significant differences at different nitrogen levels in Sphagnum palustre (p < 0.05), and different uppercase letters indicate significant differences at different nitrogen levels in Polytrichum commune (p < 0.05). * refers a significant difference between the two species (p < 0.05).
| 因素 Factor | df | 质量残留率 Mass remaining rate (%) | 总碳含量 Total carbon (C) content (%) | 总氮含量 Total nitrogen (N) content (%) | 总酚含量 Total polyphenol content (%) | 碳氮比 C:N | 总酚:氮 Total phenolics:N | 灰分含量 Ash content (%) | |||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| F | p | F | p | F | p | F | p | F | p | F | p | F | p | ||
| 氮沉降 Nitrogen deposition | 3 | 7.617 | 0.001 | 10.63 | <0.001 | 2.769 | 0.045 | 6.607 | <0.001 | 2.747 | 0.046 | 2.939 | 0.036 | 1.085 | 0.358 |
| 分解时间 Decomposition time | 4 | 52.281 | 0.001 | 140.99 | <0.001 | 40.725 | <0.001 | 79.714 | <0.001 | 14.593 | <0.001 | 218.590 | <0.001 | 2.541 | 0.043 |
| 物种 Species | 1 | 222.556 | <0.001 | 257.46 | <0.001 | 53.950 | <0.001 | 14.674 | <0.001 | 97.856 | <0.001 | 213.010 | <0.001 | 0.563 | 0.048 |
| 氮沉降×物种 Nitrogen deposition × species | 3 | 4.154 | 0.008 | 9.32 | <0.001 | 4.811 | 0.003 | 1.684 | 0.174 | 4.507 | 0.005 | 0.576 | 0.632 | 0.871 | 0.458 |
| 氮沉降×分解时间 Nitrogen deposition × decomposition time | 12 | 4.073 | <0.001 | 1.43 | 0.163 | 3.137 | 0.001 | 2.238 | 0.014 | 3.017 | 0.001 | 2.752 | 0.002 | 0.949 | 0.502 |
| 物种×分解时间 Species × decomposition time | 4 | 27.864 | <0.001 | 15.49 | <0.001 | 55.146 | <0.001 | 12.199 | <0.001 | 20.915 | <0.001 | 199.327 | <0.001 | 0.635 | 0.639 |
| 氮沉降×物种×分解时间 Nitrogen deposition × species × decomposition time | 12 | 2.175 | 0.017 | 4.127 | <0.001 | 1.336 | 0.207 | 2.429 | 0.007 | 1.743 | 0.066 | 2.535 | 0.005 | 0.899 | 0.550 |
表4 凋落物的分解指标在氮沉降、分解时间及物种间的多因素方差分析
Table 4 Multivariate analysis of variance on the differences in the decomposing indicators of two bryophytes litters among nitrogen deposition, species and decomposition time
| 因素 Factor | df | 质量残留率 Mass remaining rate (%) | 总碳含量 Total carbon (C) content (%) | 总氮含量 Total nitrogen (N) content (%) | 总酚含量 Total polyphenol content (%) | 碳氮比 C:N | 总酚:氮 Total phenolics:N | 灰分含量 Ash content (%) | |||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| F | p | F | p | F | p | F | p | F | p | F | p | F | p | ||
| 氮沉降 Nitrogen deposition | 3 | 7.617 | 0.001 | 10.63 | <0.001 | 2.769 | 0.045 | 6.607 | <0.001 | 2.747 | 0.046 | 2.939 | 0.036 | 1.085 | 0.358 |
| 分解时间 Decomposition time | 4 | 52.281 | 0.001 | 140.99 | <0.001 | 40.725 | <0.001 | 79.714 | <0.001 | 14.593 | <0.001 | 218.590 | <0.001 | 2.541 | 0.043 |
| 物种 Species | 1 | 222.556 | <0.001 | 257.46 | <0.001 | 53.950 | <0.001 | 14.674 | <0.001 | 97.856 | <0.001 | 213.010 | <0.001 | 0.563 | 0.048 |
| 氮沉降×物种 Nitrogen deposition × species | 3 | 4.154 | 0.008 | 9.32 | <0.001 | 4.811 | 0.003 | 1.684 | 0.174 | 4.507 | 0.005 | 0.576 | 0.632 | 0.871 | 0.458 |
| 氮沉降×分解时间 Nitrogen deposition × decomposition time | 12 | 4.073 | <0.001 | 1.43 | 0.163 | 3.137 | 0.001 | 2.238 | 0.014 | 3.017 | 0.001 | 2.752 | 0.002 | 0.949 | 0.502 |
| 物种×分解时间 Species × decomposition time | 4 | 27.864 | <0.001 | 15.49 | <0.001 | 55.146 | <0.001 | 12.199 | <0.001 | 20.915 | <0.001 | 199.327 | <0.001 | 0.635 | 0.639 |
| 氮沉降×物种×分解时间 Nitrogen deposition × species × decomposition time | 12 | 2.175 | 0.017 | 4.127 | <0.001 | 1.336 | 0.207 | 2.429 | 0.007 | 1.743 | 0.066 | 2.535 | 0.005 | 0.899 | 0.550 |
图3 模拟氮沉降对泥炭藓(A)和金发藓(B)凋落物质量残留率的影响(平均值±标准误, n = 4)。N0、N3、N6及N12分别表示氮添加浓度为0、3、6及12 g·m-2·a-1。不同小写字母表示同一时间内不同氮浓度间差异显著(p < 0.05)。
Fig. 3 Effects of simulated nitrogen deposition on remaining rate of Sphagnum palustre (A) and Polytrichum commune (B) litters (mean ± SE, n = 4). N0, N3, N6 and N12 represent nitrogen addition concentrations of 0, 3, 6 and 12 g·m-2·a-1, respectively. Different lowercase letters indicate significant differences at different nitrogen level at the same time periods (p < 0.05).
图4 模拟氮沉降对泥炭藓(A、C、E)和金发藓(B、D、F)凋落物元素含量的影响(平均值±标准误, n = 4)。N0、N3、N6及N12分别表示氮添加浓度为0、3、6及12 g·m-2·a-1。不同小写字母表示同一时间内不同氮浓度间差异显著(p < 0.05)。
Fig. 4 Effects of simulated nitrogen deposition on element contents of the Sphagnum palustre (A, C, E) and Polytrichum commune (B, D, F) (mean ± SE, n = 4). N0, N3, N6 and N12 represent nitrogen addition concentrations of 0, 3, 6 and 12 g·m-2·a-1, respectively. Different lowercase letters indicate significant differences at different nitrogen level at the same time periods (p < 0.05).
图5 模拟氮沉降对泥炭藓(A、C)和金发藓(B、D)凋落物化学计量比的影响(平均值±标准误, n = 4)。N0、N3、N6及N12分别表示氮添加浓度为0、3、6及12 g·m-2·a-1。不同小写字母表示同一时间内不同氮浓度间差异显著(p < 0.05)。
Fig. 5 Effects of simulated nitrogen deposition on element ratios of the Sphagnum palustre (A, C) and Polytrichum commune (B, D) litters (mean ± SE, n = 4). N0, N3, N6 and N12 represent nitrogen addition concentrations of 0, 3, 6 and 12 g·m-2·a-1, respectively. Different lowercase letters indicate significant differences at different nitrogen level at the same time periods (p < 0.05).
图6 模拟氮沉降对泥炭藓(A)和金发藓(B)凋落物灰分含量的影响(平均值±标准误, n = 4)。N0、N3、N6及N12分别表示氮添加浓度为0、3、6及12 g·m-2·a-1。不同小写字母表示同一时间内不同氮浓度间差异显著(p < 0.05)。
Fig. 6 Effects of simulated nitrogen deposition on ash content of Sphagnum palustre (A) and Polytrichum commune (B) litters (mean ± SE, n = 4). N0, N3, N6 and N12 represent nitrogen addition concentrations of 0, 3, 6 and 12 g·m-2·a-1, respectively. Different lowercase letters indicate significant differences at different nitrogen level at the same time periods (p < 0.05).
图7 模拟氮沉降对泥炭藓氮含量的影响(平均值±标准误, n = 4)。不同小写字母表示不同氮处理间差异显著(p < 0.05)。
Fig. 7 Effects of simulated nitrogen deposition on the total nitrogen content of Sphagnum palustre (mean ± SE, n = 4). Different lowercase letters indicate significant differences at different nitrogen levels (p < 0.05).
图8 苔藓植物初始化学组分与凋落物分解指标的相关性。*, p < 0.05; **, p < 0.01; ***, p < 0.001。
Fig. 8 Correlation between the initial chemical traits and the decomposition indicators of two bryophytes litters. *, p < 0.05; **, p < 0.01; ***, p < 0.001。
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