植物生态学报 ›› 2012, Vol. 36 ›› Issue (8): 763-773.DOI: 10.3724/SP.J.1258.2012.00763
王国栋1,2, 吕宪国1, 姜明1,*(), 王铭1,2, 赵魁义1, 娄彦景1
收稿日期:
2012-01-09
接受日期:
2012-04-25
出版日期:
2012-01-09
发布日期:
2012-08-21
通讯作者:
姜明
作者简介:
* (E-mail: jiangm@neigae.ac.cn)
WANG Guo-Dong1,2, LÜ Xian-Guo1, JIANG Ming1,*(), WANG Ming1,2, ZHAO Kui-Yi1, LOU Yan-Jing1
Received:
2012-01-09
Accepted:
2012-04-25
Online:
2012-01-09
Published:
2012-08-21
Contact:
JIANG Ming
摘要:
通过幼苗萌发法和样方调查相结合的方法对三江平原不同演替恢复阶段的种子库特征及其与植被的关系进行了研究。将开垦湿地、不同演替恢复阶段湿地以及天然湿地不同土壤层次(0-5、5-10 cm和根茎)的种子库在两种水分条件下(湿润、淹水10 cm)进行萌发处理。结果表明: 随着演替恢复阶段的进行, 种子库的结构和规模逐渐扩大, 地表群落表现出由旱生物种占优势的群落逐渐演变成以小叶章(Calamagrostis angustifolia)占优势的湿生群落的演替趋势。恢复7年湿地、恢复14年湿地、天然湿地土壤种子库萌发物种数分别为24种、29种、39种, 植被物种数为21种、25种、14种。湿地类型、水分条件和土壤层次均显著影响种子库萌发的物种数及幼苗数(p < 0.01)。种子库具有明显的分层现象, 天然湿地0-5 cm土层种子库种子萌发密度是5-10 cm土层的4倍左右, 而恢复湿地仅1.3倍左右, 且土层间萌发物种相似性系数较低。湿润条件下的萌发物种数显著高于淹水条件, 且两种水分条件下萌发物种的生活型不同。由于恢复时间较短, 不同演替恢复阶段的种子库与植被相似性维持在30%以下。湿地中根茎分蘖出大量的湿地物种, 对于小叶章等优势物种的繁殖具有重要作用。研究表明, 在开垦湿地退耕后的次生演替阶段, 种子库能够保持大量的湿地物种, 通过对湿地种子库与植被的关系研究, 能够为三江平原湿地群落演替与湿地恢复提供策略指导。
王国栋, 吕宪国, 姜明, 王铭, 赵魁义, 娄彦景. 三江平原恢复湿地土壤种子库特征及其与植被的关系. 植物生态学报, 2012, 36(8): 763-773. DOI: 10.3724/SP.J.1258.2012.00763
WANG Guo-Dong, LÜ Xian-Guo, JIANG Ming, WANG Ming, ZHAO Kui-Yi, LOU Yan-Jing. Characteristics of the soil seed banks and relationships with the vegetation in restored wetlands in Sanjiang Plain, northeast of China. Chinese Journal of Plant Ecology, 2012, 36(8): 763-773. DOI: 10.3724/SP.J.1258.2012.00763
生活型 Life form | 物种 Species | 种子密度 Seed density (individuals·m-2) | |||
---|---|---|---|---|---|
开垦湿地 FW | 恢复7年湿地 RW-7 | 恢复14年湿地 RW-14 | 天然湿地 NW | ||
灌木 | 细叶沼柳 Salix rosmarinifolia | 16 ± 16 | 144 ± 41 (64) | 256 ± 98 (80) | 244 ± 49 (40) |
Shrub | 越桔柳 Salix myrtilloides | 0 | 16 ± 16 | 32 ± 32 | 8 ± 8 |
粉花绣线菊 Spiraea japonica | 0 | 0 | 16 ± 16 (16) | 96 ± 37 (56) | |
多年生草本 | 小叶章 Calamagrostis angustifolia | 0 | 160 ± 40 (16) | 608 ± 115 (288) | 856 ± 209 (376) |
Perennial herb | 湿薹草 Carex humida | 0 | 0 | 0 | 64 ± 29 (56) |
薹草 Carex dispalata | 0 | 0 | 96 ± 30 (16) | 8 ± 8 | |
毛薹草 Carex duriuscula | 0 | 0 | 0 | 8 ± 8 | |
球尾花 Lysimachia thyrsiflora | 0 | 64 ± 47 | 0 | 0 | |
五脉山黧豆 Lathyrus quinquenervius | 0 | 0 | 0 | 40 ± 27 (40) | |
水苏 Stachys japonica | 0 | 64 ± 21 (16) | 16 ± 8 (16) | 24 ± 12 | |
三裂慈菇 Sagittaria trifolia | 0 | 16 ± 16 | 0 | 0 | |
龙江凤毛菊 Saussurea amurensis | 16 ± 16 | 0 | 288 ± 162 | 40 ± 40 (40) | |
宽叶香蒲 Typha latifolia | 160 ± 59 | 176 ± 45 | 144 ± 49 (64) | 200 ± 35 (24) | |
苣荬菜 Sonchus brachyotus | 0 | 0 | 48 ± 32 | 128 ± 66 (48) | |
线叶黑三棱 Sparganium angustifolium | 0 | 0 | 0 | 72 ± 29 | |
菹草 Potamogeton crispus | 96 ± 40 | 192 ± 80 | 825 ± 360 | 160 ± 16 | |
沼泽早熟禾 Poa palustris | 0 | 384 ± 108 (112) | 112 ± 80 | 16 ± 10 | |
灯芯草 Juncus effusus | 0 | 1712 ± 825 (224) | 464 ± 203 (32) | 16 ± 10 | |
地瓜苗 Lycopus lucidus | 0 | 80 ± 29 (64) | 32 ± 20 (16) | 0 | |
老鹳草 Geranium wilfordii | 0 | 0 | 48 ± 48 (48) | 0 | |
泽芹 Sium suave | 0 | 48 ± 48 (48) | 0 | 0 | |
垂穗粉花地榆 Sanguisorba tenuifolia | 0 | 96 ± 49 (48) | 0 | 16 ± 16 (16) | |
山酢浆草 Oxalis acetosella | 0 | 16 ± 16 (16) | 0 | 0 | |
兴安拉拉藤 Galium dahuricum | 0 | 0 | 0 | 8 ± 8 | |
堇菜 Viola verecunda | 0 | 16 ± 16 (16) | 0 | 8 ± 8 | |
东北婆婆纳 Veronica rotunda | 0 | 16 ± 16 (16) | 0 | 72 ± 42 (32) | |
车前 Plantago asiatica | 0 | 0 | 0 | 8 ± 8 | |
牛鞭草 Hemarthria sibirica | 0 | 0 | 80 ± 29 | 24 ± 17 | |
乌腺金丝桃 Hepericum attenuatum | 0 | 48 ± 32 (16) | 16 ± 16 | 8 ± 8 | |
苦草 Vallisneria spiralis | 0 | 0 | 0 | 8 ± 8 | |
鳞毛羽节蕨 Gymnocarpium dryopteris | 80 ± 16 | 1216 ± 429 (232) | 2896 ± 1374 (50) | 5280 ± 2475 (1624) | |
还阳参 Crepis crocea | 0 | 0 | 96 ± 35 (16) | 80 ± 37 (32) | |
草莓 Fragaria ananassa | 0 | 0 | 0 | 8 ± 8 | |
苋属一种 Amaranthus sp. | 0 | 0 | 16 ± 16 (16) | 0 | |
大活 Angelica dahurica | 0 | 208 ± 72 (64) | 144 ± 73 (32) | 112 ± 49 (16) | |
金鱼藻 Ceratophyllum demersum | 0 | 0 | 16 ± 16 | 216 ± 115 | |
宽叶山蒿 Artemisia stolonifera | 0 | 0 | 64 ± 32 (20) | 8 ± 8 | |
一、二年生草本 | 赛繁缕 Stellaria neglecta | 0 | 16 ± 16 | 80 ± 80 | 8 ± 8 |
One biennial herb | 东北鼠曲草 Gnaphalium mandshuricum | 16 ± 8 | 176 ± 109 | 272 ± 94 | 304 ± 155 |
野稗 Echinochloa crusgalli | 16 ± 8 | 0 | 96 ± 24 | 104 ± 52 | |
荠菜 Capsella bursa-pastoris | 32 ± 16 | 352 ± 314 | 752 ± 497 | 288 ± 116 | |
卵穗荸荠 Eleocharis ovata | 0 | 144 ± 98 | 16 ± 16 | 16 ± 10 | |
水蓼 Polygonum hydropiper | 0 | 0 | 0 | 24 ± 12 | |
芒剪股颖 Agrostis trinii | 0 | 0 | 0 | 16 ± 16 | |
灰绿藜 Chenopodium glaucum | 0 | 16 ± 16 | 48 ± 21 | 48 ± 25 | |
狗尾草 Setaria viridis | 0 | 0 | 48 ± 21 | 8 ± 8 | |
总数 Total | 432 ± 51 | 5376 ± 1042 (952) | 7625 ± 1213 (690) | 8632 ± 1526 (2400) |
表1 三江平原开垦湿地、恢复湿地与天然湿地的种子库萌发物种及种子密度(平均值±标准误差)
Table 1 Germination species and seed density of farmed wetland, restored wetlands and natural wetlands in the Sanjiang Plain (mean ± SE)
生活型 Life form | 物种 Species | 种子密度 Seed density (individuals·m-2) | |||
---|---|---|---|---|---|
开垦湿地 FW | 恢复7年湿地 RW-7 | 恢复14年湿地 RW-14 | 天然湿地 NW | ||
灌木 | 细叶沼柳 Salix rosmarinifolia | 16 ± 16 | 144 ± 41 (64) | 256 ± 98 (80) | 244 ± 49 (40) |
Shrub | 越桔柳 Salix myrtilloides | 0 | 16 ± 16 | 32 ± 32 | 8 ± 8 |
粉花绣线菊 Spiraea japonica | 0 | 0 | 16 ± 16 (16) | 96 ± 37 (56) | |
多年生草本 | 小叶章 Calamagrostis angustifolia | 0 | 160 ± 40 (16) | 608 ± 115 (288) | 856 ± 209 (376) |
Perennial herb | 湿薹草 Carex humida | 0 | 0 | 0 | 64 ± 29 (56) |
薹草 Carex dispalata | 0 | 0 | 96 ± 30 (16) | 8 ± 8 | |
毛薹草 Carex duriuscula | 0 | 0 | 0 | 8 ± 8 | |
球尾花 Lysimachia thyrsiflora | 0 | 64 ± 47 | 0 | 0 | |
五脉山黧豆 Lathyrus quinquenervius | 0 | 0 | 0 | 40 ± 27 (40) | |
水苏 Stachys japonica | 0 | 64 ± 21 (16) | 16 ± 8 (16) | 24 ± 12 | |
三裂慈菇 Sagittaria trifolia | 0 | 16 ± 16 | 0 | 0 | |
龙江凤毛菊 Saussurea amurensis | 16 ± 16 | 0 | 288 ± 162 | 40 ± 40 (40) | |
宽叶香蒲 Typha latifolia | 160 ± 59 | 176 ± 45 | 144 ± 49 (64) | 200 ± 35 (24) | |
苣荬菜 Sonchus brachyotus | 0 | 0 | 48 ± 32 | 128 ± 66 (48) | |
线叶黑三棱 Sparganium angustifolium | 0 | 0 | 0 | 72 ± 29 | |
菹草 Potamogeton crispus | 96 ± 40 | 192 ± 80 | 825 ± 360 | 160 ± 16 | |
沼泽早熟禾 Poa palustris | 0 | 384 ± 108 (112) | 112 ± 80 | 16 ± 10 | |
灯芯草 Juncus effusus | 0 | 1712 ± 825 (224) | 464 ± 203 (32) | 16 ± 10 | |
地瓜苗 Lycopus lucidus | 0 | 80 ± 29 (64) | 32 ± 20 (16) | 0 | |
老鹳草 Geranium wilfordii | 0 | 0 | 48 ± 48 (48) | 0 | |
泽芹 Sium suave | 0 | 48 ± 48 (48) | 0 | 0 | |
垂穗粉花地榆 Sanguisorba tenuifolia | 0 | 96 ± 49 (48) | 0 | 16 ± 16 (16) | |
山酢浆草 Oxalis acetosella | 0 | 16 ± 16 (16) | 0 | 0 | |
兴安拉拉藤 Galium dahuricum | 0 | 0 | 0 | 8 ± 8 | |
堇菜 Viola verecunda | 0 | 16 ± 16 (16) | 0 | 8 ± 8 | |
东北婆婆纳 Veronica rotunda | 0 | 16 ± 16 (16) | 0 | 72 ± 42 (32) | |
车前 Plantago asiatica | 0 | 0 | 0 | 8 ± 8 | |
牛鞭草 Hemarthria sibirica | 0 | 0 | 80 ± 29 | 24 ± 17 | |
乌腺金丝桃 Hepericum attenuatum | 0 | 48 ± 32 (16) | 16 ± 16 | 8 ± 8 | |
苦草 Vallisneria spiralis | 0 | 0 | 0 | 8 ± 8 | |
鳞毛羽节蕨 Gymnocarpium dryopteris | 80 ± 16 | 1216 ± 429 (232) | 2896 ± 1374 (50) | 5280 ± 2475 (1624) | |
还阳参 Crepis crocea | 0 | 0 | 96 ± 35 (16) | 80 ± 37 (32) | |
草莓 Fragaria ananassa | 0 | 0 | 0 | 8 ± 8 | |
苋属一种 Amaranthus sp. | 0 | 0 | 16 ± 16 (16) | 0 | |
大活 Angelica dahurica | 0 | 208 ± 72 (64) | 144 ± 73 (32) | 112 ± 49 (16) | |
金鱼藻 Ceratophyllum demersum | 0 | 0 | 16 ± 16 | 216 ± 115 | |
宽叶山蒿 Artemisia stolonifera | 0 | 0 | 64 ± 32 (20) | 8 ± 8 | |
一、二年生草本 | 赛繁缕 Stellaria neglecta | 0 | 16 ± 16 | 80 ± 80 | 8 ± 8 |
One biennial herb | 东北鼠曲草 Gnaphalium mandshuricum | 16 ± 8 | 176 ± 109 | 272 ± 94 | 304 ± 155 |
野稗 Echinochloa crusgalli | 16 ± 8 | 0 | 96 ± 24 | 104 ± 52 | |
荠菜 Capsella bursa-pastoris | 32 ± 16 | 352 ± 314 | 752 ± 497 | 288 ± 116 | |
卵穗荸荠 Eleocharis ovata | 0 | 144 ± 98 | 16 ± 16 | 16 ± 10 | |
水蓼 Polygonum hydropiper | 0 | 0 | 0 | 24 ± 12 | |
芒剪股颖 Agrostis trinii | 0 | 0 | 0 | 16 ± 16 | |
灰绿藜 Chenopodium glaucum | 0 | 16 ± 16 | 48 ± 21 | 48 ± 25 | |
狗尾草 Setaria viridis | 0 | 0 | 48 ± 21 | 8 ± 8 | |
总数 Total | 432 ± 51 | 5376 ± 1042 (952) | 7625 ± 1213 (690) | 8632 ± 1526 (2400) |
物种平均数 Mean number of species | 幼苗数 Number of seedlings | |||
---|---|---|---|---|
F | p | F | p | |
湿地类型 Wetland type (wt) | 42.880 | < 0.001** | 24.138 | < 0.001** |
水分条件 Water regime (wr) | 481.945 | < 0.001** | 246.576 | < 0.001** |
土壤层次 Soil layer (sl) | 20.770 | < 0.001** | 21.920 | < 0.001** |
湿地类型×水分条件 wt × wr | 32.467 | < 0.001** | 13.088 | < 0.001** |
湿地类型×土壤层次 wt × sl | 1.759 | 0.111 | 1.774 | 0.108 |
水分条件×土壤层次 wr × sl | 1.788 | 0.171 | 10.304 | < 0.001** |
湿地类型×水分条件×土壤层次 wt × wr × db | 1.848 | 0.093 | 1.651 | 0.137 |
表2 湿地类型、水分条件和土壤层次对湿地种子库萌发物种平均数及幼苗数影响的三因素方差分析
Table 2 Analysis of variance (three-way ANOVA) on the effects of wetland type, water regime and soil layer for mean number of germination species and seedling emergence from seed bank of wetland
物种平均数 Mean number of species | 幼苗数 Number of seedlings | |||
---|---|---|---|---|
F | p | F | p | |
湿地类型 Wetland type (wt) | 42.880 | < 0.001** | 24.138 | < 0.001** |
水分条件 Water regime (wr) | 481.945 | < 0.001** | 246.576 | < 0.001** |
土壤层次 Soil layer (sl) | 20.770 | < 0.001** | 21.920 | < 0.001** |
湿地类型×水分条件 wt × wr | 32.467 | < 0.001** | 13.088 | < 0.001** |
湿地类型×土壤层次 wt × sl | 1.759 | 0.111 | 1.774 | 0.108 |
水分条件×土壤层次 wr × sl | 1.788 | 0.171 | 10.304 | < 0.001** |
湿地类型×水分条件×土壤层次 wt × wr × db | 1.848 | 0.093 | 1.651 | 0.137 |
图1 水分条件、土壤层次对不同恢复演替阶段湿地平均萌发物种数的影响(平均值±标准误差)。FW, 开垦湿地; RW-7, 恢复7年湿地; RW-14, 恢复14年湿地; NW, 天然湿地.
Fig. 1 Effects of water regime and soil layer on mean number of species in different restoration succession stages (mean ± SE). FW, farmed wetland; RW-7, 7-year restored wetland; RW-14, 14-year restored wetland; NW, natural wetland.
图2 水分条件、土壤层次对不同恢复演替阶段湿地平均萌发幼苗数的影响(平均值±标准误差)。FW, 开垦湿地; RW-7, 恢复7年湿地; RW-14, 恢复14年湿地; NW, 天然湿地。
Fig. 2 Effects of water regime and soil layer on mean number of seedlings in different restoration succession stages (mean ± SE). FW, farmed wetland; RW-7, 7-year restored wetland; RW-14, 14-year restored wetland; NW, natural wetland.
物种 Species | 湿地类型 Wetland type | ||
---|---|---|---|
天然湿地 NW | 恢复7年 RW-7 | 恢复14年 RW-14 | |
小叶章 Calamagrostis angustifoliaP | 1.882√ | 0.518√ | 1.482√ |
宽叶山蒿 Artemisia stoloniferP | 0.173√ | 0.672 | 0.421√ |
垂穗粉花地榆 Sanguisorba tenuifoliaP | 0.087√ | 0.238 | |
芦苇 Phragmites communisP | 0.085 | 0.239 | 0.052 |
粉花绣线菊 Spiraea japonicaP | 0.060√ | 0.241 | |
地瓜苗 Lycopus lucidusP | 0.042 | 0.061√ | |
野火球 Trilolium lupinasterP | 0.039 | 0.003 | |
赛繁缕 Stellaria neglectaa | 0.036 | 0.041√ | 0.011√ |
草莓 Fragaria ananassaP | 0.033√ | 0.038 | 0.057 |
越桔柳 Salix myrtilloidesP | 0.033√ | 0.037√ | |
苣荬菜 Sonchus brachyotusP | 0.028√ | 0.032 | |
兴安拉拉藤 Galium dahuricumP | 0.027√ | 0.003 | |
沼泽早熟禾 Poa palustrisP | 0.02√ | 0.215√ | 0.172√ |
毛薹草 Carex duriusculaP | 0.003√ | 0.072 | |
球尾花 Lysimachia thyrsifloraP | 0.007√ | 0.003 | |
山杨 Populus davidianaP | 0.152 | 0.172 | |
毒芹 Cicuta virosaP | 0.007 | 0.013 | |
千屈菜 Lythrum salicariaP | 0.203 | 0.132 | |
山酢浆草 Oxalis acetosellaP | 0.003√ | ||
细叶沼柳 Salix rosmarinifoliaP | 0.083√ | 0.152√ | |
东北鼠曲草 Gnaphalium mandshuricuma | 0.010√ | 0.013√ | |
灰绿黎 Chenopodium glaucuma | 0.003√ | 0.006√ | |
黄莲花 Lysimachia davuricaP | 0.007 | ||
泽芹 Sium suaveP | 0.003√ | 0.003 | |
问荆 Equisetum arvenseP | 0.054 | 0.003 | |
狭叶黄岑 Scutellaria regelianaP | 0.008 | 0.025 | |
五脉山黧豆 Lathyrus quinquenerviusP | 0.113 | ||
野大豆 Glycine sojaa | 0.004 | ||
柳蒿 Artemisia integrifoliaP | 0.007 | ||
老鹳草 Geranium wilfordiiP | 0.015√ |
表3 不同演替恢复阶段植被物种组成及重要值
Table 3 Species composition and important value of vegetation in different restoration succession stages
物种 Species | 湿地类型 Wetland type | ||
---|---|---|---|
天然湿地 NW | 恢复7年 RW-7 | 恢复14年 RW-14 | |
小叶章 Calamagrostis angustifoliaP | 1.882√ | 0.518√ | 1.482√ |
宽叶山蒿 Artemisia stoloniferP | 0.173√ | 0.672 | 0.421√ |
垂穗粉花地榆 Sanguisorba tenuifoliaP | 0.087√ | 0.238 | |
芦苇 Phragmites communisP | 0.085 | 0.239 | 0.052 |
粉花绣线菊 Spiraea japonicaP | 0.060√ | 0.241 | |
地瓜苗 Lycopus lucidusP | 0.042 | 0.061√ | |
野火球 Trilolium lupinasterP | 0.039 | 0.003 | |
赛繁缕 Stellaria neglectaa | 0.036 | 0.041√ | 0.011√ |
草莓 Fragaria ananassaP | 0.033√ | 0.038 | 0.057 |
越桔柳 Salix myrtilloidesP | 0.033√ | 0.037√ | |
苣荬菜 Sonchus brachyotusP | 0.028√ | 0.032 | |
兴安拉拉藤 Galium dahuricumP | 0.027√ | 0.003 | |
沼泽早熟禾 Poa palustrisP | 0.02√ | 0.215√ | 0.172√ |
毛薹草 Carex duriusculaP | 0.003√ | 0.072 | |
球尾花 Lysimachia thyrsifloraP | 0.007√ | 0.003 | |
山杨 Populus davidianaP | 0.152 | 0.172 | |
毒芹 Cicuta virosaP | 0.007 | 0.013 | |
千屈菜 Lythrum salicariaP | 0.203 | 0.132 | |
山酢浆草 Oxalis acetosellaP | 0.003√ | ||
细叶沼柳 Salix rosmarinifoliaP | 0.083√ | 0.152√ | |
东北鼠曲草 Gnaphalium mandshuricuma | 0.010√ | 0.013√ | |
灰绿黎 Chenopodium glaucuma | 0.003√ | 0.006√ | |
黄莲花 Lysimachia davuricaP | 0.007 | ||
泽芹 Sium suaveP | 0.003√ | 0.003 | |
问荆 Equisetum arvenseP | 0.054 | 0.003 | |
狭叶黄岑 Scutellaria regelianaP | 0.008 | 0.025 | |
五脉山黧豆 Lathyrus quinquenerviusP | 0.113 | ||
野大豆 Glycine sojaa | 0.004 | ||
柳蒿 Artemisia integrifoliaP | 0.007 | ||
老鹳草 Geranium wilfordiiP | 0.015√ |
植被 Vegetation | 种子库 Seed bank | ||||||
---|---|---|---|---|---|---|---|
恢复7年湿地RW-7 | 恢复14年湿地 RW-14 | 天然湿地 NW | 恢复7年湿地 RW-7 | 恢复14年湿地 RW-14 | 天然湿地 NW | ||
恢复7年湿地 RW-7 | 1.00 | 0.53 | 0.35 | 1.00 | 0.47 | 0.43 | |
恢复14年湿地 RW-14 | 1.00 | 0.39 | 1.00 | 0.62 | |||
天然湿地 NW | 1.00 | 1.00 |
表4 天然湿地与恢复湿地的植被物种及种子库的相似性系数
Table 4 Similarity coefficient of the vegetation species and seed banks between natural and restored wetlands
植被 Vegetation | 种子库 Seed bank | ||||||
---|---|---|---|---|---|---|---|
恢复7年湿地RW-7 | 恢复14年湿地 RW-14 | 天然湿地 NW | 恢复7年湿地 RW-7 | 恢复14年湿地 RW-14 | 天然湿地 NW | ||
恢复7年湿地 RW-7 | 1.00 | 0.53 | 0.35 | 1.00 | 0.47 | 0.43 | |
恢复14年湿地 RW-14 | 1.00 | 0.39 | 1.00 | 0.62 | |||
天然湿地 NW | 1.00 | 1.00 |
湿地类型 Wetland type | 植被 Vegetation | 种子库 Seed bank | 共有物种数 Common species | 相似性系数 Similarity coefficient |
---|---|---|---|---|
恢复7年湿地 RW-7 | 21 | 24 | 9 | 0.25 |
恢复14年湿地 RW-14 | 25 | 29 | 10 | 0.23 |
天然湿地 NW | 14 | 39 | 10 | 0.23 |
表5 种子库与植被相似性
Table 5 Similarity of the seed bank and standing vegetation
湿地类型 Wetland type | 植被 Vegetation | 种子库 Seed bank | 共有物种数 Common species | 相似性系数 Similarity coefficient |
---|---|---|---|---|
恢复7年湿地 RW-7 | 21 | 24 | 9 | 0.25 |
恢复14年湿地 RW-14 | 25 | 29 | 10 | 0.23 |
天然湿地 NW | 14 | 39 | 10 | 0.23 |
图3 天然湿地与恢复湿地植被及种子库物种多样性指数。RW-7, 恢复7年湿地; RW-14, 恢复14年湿地; NW, 天然湿地。
Fig. 3 Diversity indexes of the vegetation and seed bank in the natural and restored wetlands. RW-7, 7-year restored wetland; RW-14, 14-year restored wetland; NW, natural wetland.
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