生物多样性 ›› 2016, Vol. 24 ›› Issue (10): 1093-1104. DOI: 10.17520/biods.2015341
郭印1,2, 王云泉1,2, 陈磊2,*(), 米湘成2, 任海保2, 陈声文3, 陈建华1,*()
收稿日期:
2015-12-03
接受日期:
2016-10-19
出版日期:
2016-10-20
发布日期:
2016-11-10
通讯作者:
陈磊,陈建华
基金资助:
Yin Guo1,2, Yunquan Wang1,2, Lei Chen2,*(), Xiangcheng Mi2, Haibao Ren2, Shengwen Chen3, Jianhua Chen1,*()
Received:
2015-12-03
Accepted:
2016-10-19
Online:
2016-10-20
Published:
2016-11-10
Contact:
Chen Lei,Chen Jianhua
摘要:
幼苗阶段是森林群落更新的瓶颈, 研究木本植物幼苗组成和分布格局对正确认识森林群落构建以及多样性维持机制具有十分重要的意义。以往基于幼苗阶段的研究取样强度较小, 主要涉及常见种, 缺乏对稀有种的有效监测。我们对古田山24 ha森林样地幼苗监测网络进行了扩建, 在已有507个1 m × 1 m幼苗监测样方的基础上, 增设了285个5 m × 5 m幼苗样方, 对样方内所有高度≥ 10 cm且胸径< 1 cm的木本植物幼苗按大样地监测标准进行了定位、挂牌、鉴定和测量。本研究利用2012年5 m × 5 m幼苗监测样方的首次调查数据, 比较了24 ha大样地中不同取样强度下幼苗和非幼苗(胸径≥ 1 cm的木本植物)个体在物种组成、多样性分布格局以及生境偏好等方面的差异。结果表明: (1) 285个5 m × 5 m幼苗监测样方共计有木本植物幼苗138种20,581株, Shannon-Wiener多样性指数以及经多度校正的物种丰富度指数均显著高于1 m × 1 m幼苗监测样方以及24 ha大样地的非幼苗个体, 该结果与基于Rarefaction方法计算的物种数期望值结果一致; 与1 m × 1 m幼苗监测样方结果相比, 5 m × 5 m幼苗监测样方内物种数-取样面积曲线趋于饱和。(2) 5 m × 5 m幼苗监测样方幼苗与24 ha大样地非幼苗个体物种多度呈异速增长关系, 表明植物在幼苗阶段受到负密度制约效应的影响, 死亡率相对较高。(3)取样强度和胸径阈值的选取对群落稀有种的界定有重要影响, 朱砂根(Ardisia crenata)、山鸡椒(Litsea cubeba)、美丽胡枝子(Lespedeza thunbergii subsp. formosa)等物种在24 ha样地水平被认为是稀有种, 但是在5 m × 5 m幼苗样方却属于常见种。(4)指示种分析结果表明, 基于不同取样强度的幼苗生境指示种与基于大样地非幼苗个体的分析结果存在较大差异。在5 m × 5 m幼苗样方中, 13个物种与单一生境类型显著相关, 其中仅有3个物种与1 m × 1 m幼苗样方指示种相同, 与24 ha大样地非幼苗相比, 仅有2个共有指示种。总之, 不同取样强度可显著影响幼苗物种多样性格局的分析结果, 通过样方扩建对林下幼苗进行系统监测, 可进一步加深对群落生物多样性维持机制的认识。
郭印, 王云泉, 陈磊, 米湘成, 任海保, 陈声文, 陈建华 (2016) 不同取样强度下古田山木本植物幼苗组成 及其分布格局比较. 生物多样性, 24, 1093-1104. DOI: 10.17520/biods.2015341.
Yin Guo, Yunquan Wang, Lei Chen, Xiangcheng Mi, Haibao Ren, Shengwen Chen, Jianhua Chen (2016) Comparing tree seedling composition and distribution patterns under different sampling intensities in the 24 ha Gutianshan forest dynamics plot. Biodiversity Science, 24, 1093-1104. DOI: 10.17520/biods.2015341.
物种名 Species | 科名 Family | 个体数 No. of individuals | 重要值 IV (%) | 生活型 Life form |
---|---|---|---|---|
甜槠 Castanopsis eyrei | 壳斗科 Fagaceae | 4,110 | 24.85 | 常绿 Evergreen |
拟赤杨 Alniphyllum fortunei | 安息香科 Styracaceae | 1,448 | 9.95 | 落叶 Deciduous |
虎皮楠 Daphniphyllum pentandrum | 虎皮楠科 Daphniphyllaceae | 949 | 7.67 | 常绿 Evergreen |
赤楠 Syzygium buxifolium | 桃金娘科 Myrtaceae | 900 | 7.51 | 常绿 Evergreen |
浙江新木姜子 Neolitsea aurata var. chekiangensis | 樟科 Lauraceae | 791 | 7.39 | 常绿 Evergreen |
浙江红花油茶 Camellia chekiangoleosa | 山茶科 Theaceae | 783 | 7.25 | 常绿 Evergreen |
柳叶蜡梅 Chimonanthus nitens | 蜡梅科 Calycanthaceae | 688 | 6.74 | 落叶 Deciduous |
隔药柃 Eurya muricata | 山茶科 Theaceae | 625 | 6.04 | 常绿 Evergreen |
毛花连蕊茶 Camellia fraterna | 山茶科 Theaceae | 536 | 5.31 | 常绿 Evergreen |
矩形叶鼠刺 Itea omeiensis | 虎耳草科 Saxifragaceae | 583 | 4.80 | 常绿 Evergreen |
石斑木 Rhaphiolepis indica | 蔷薇科 Rosaceae | 434 | 4.78 | 常绿 Evergreen |
木荷 Schima superba | 山茶科 Theaceae | 545 | 4.76 | 常绿 Evergreen |
马银花 Rhododendron ovatum | 杜鹃花科 Ericaceae | 428 | 4.47 | 常绿 Evergreen |
杨梅叶蚊母树 Distylium myricoides | 金缕梅科 Hamamelidaceae | 627 | 4.42 | 常绿 Evergreen |
红楠 Machilus thunbergii | 樟科 Lauraceae | 293 | 3.93 | 常绿 Evergreen |
总计 Total | - | 20,581 | 200.00 | - |
表1 古田山5 m × 5 m幼苗监测样方主要物种重要值(IV)等基础信息
Table 1 The basic information of main species such as importance value (IV) in GTS 5 m × 5 m seedling plots
物种名 Species | 科名 Family | 个体数 No. of individuals | 重要值 IV (%) | 生活型 Life form |
---|---|---|---|---|
甜槠 Castanopsis eyrei | 壳斗科 Fagaceae | 4,110 | 24.85 | 常绿 Evergreen |
拟赤杨 Alniphyllum fortunei | 安息香科 Styracaceae | 1,448 | 9.95 | 落叶 Deciduous |
虎皮楠 Daphniphyllum pentandrum | 虎皮楠科 Daphniphyllaceae | 949 | 7.67 | 常绿 Evergreen |
赤楠 Syzygium buxifolium | 桃金娘科 Myrtaceae | 900 | 7.51 | 常绿 Evergreen |
浙江新木姜子 Neolitsea aurata var. chekiangensis | 樟科 Lauraceae | 791 | 7.39 | 常绿 Evergreen |
浙江红花油茶 Camellia chekiangoleosa | 山茶科 Theaceae | 783 | 7.25 | 常绿 Evergreen |
柳叶蜡梅 Chimonanthus nitens | 蜡梅科 Calycanthaceae | 688 | 6.74 | 落叶 Deciduous |
隔药柃 Eurya muricata | 山茶科 Theaceae | 625 | 6.04 | 常绿 Evergreen |
毛花连蕊茶 Camellia fraterna | 山茶科 Theaceae | 536 | 5.31 | 常绿 Evergreen |
矩形叶鼠刺 Itea omeiensis | 虎耳草科 Saxifragaceae | 583 | 4.80 | 常绿 Evergreen |
石斑木 Rhaphiolepis indica | 蔷薇科 Rosaceae | 434 | 4.78 | 常绿 Evergreen |
木荷 Schima superba | 山茶科 Theaceae | 545 | 4.76 | 常绿 Evergreen |
马银花 Rhododendron ovatum | 杜鹃花科 Ericaceae | 428 | 4.47 | 常绿 Evergreen |
杨梅叶蚊母树 Distylium myricoides | 金缕梅科 Hamamelidaceae | 627 | 4.42 | 常绿 Evergreen |
红楠 Machilus thunbergii | 樟科 Lauraceae | 293 | 3.93 | 常绿 Evergreen |
总计 Total | - | 20,581 | 200.00 | - |
图2 古田山24 ha森林动态监测样地不同取样强度下幼苗的种-面积曲线
Fig. 2 Species-area relationship of seedlings under different sampling intensities in the 24 ha GTS forest dynamics plot
类型 Type | 物种数 No. of species | 个体数 No. of individuals | Shannon-Wiener指数 Shannon-Wiener index | 抽样 Rarefraction (N = 1,000) | Pielou均匀度指数 Pielou evenness index |
---|---|---|---|---|---|
幼苗样方 seedling plots 1 m × 1 m幼苗样方 1 m × 1 m seedling plots | 118 | 4,718 | 4.03 | 84.87 | 0.53 |
5 m × 5 m幼苗样方 5 m × 5 m seedling plots 非幼苗样方 Non-seedling plots | 138 | 20,581 | 4.25 | 89.22 | 0.49 |
1 cm ≤ DBH < 2.5 cm | 144 | 70,916 | 4.11 | 71.83 | 0.42 |
2.5 cm ≤ DBH < 7.5 cm | 132 | 45,524 | 4.05 | 72.23 | 0.43 |
7.5 cm ≤ DBH < 22.5 cm | 115 | 17,835 | 3.81 | 66.70 | 0.42 |
DBH ≥ 22.5 cm | 63 | 6,425 | 2.63 | 35.65 | 0.33 |
表2 古田山24 ha森林监测样地中幼苗与非幼苗的物种多样性比较
Table 2 Comparison of species diversity of seedling and non-seedling plots in the 24 ha GTS forest dynamics plot
类型 Type | 物种数 No. of species | 个体数 No. of individuals | Shannon-Wiener指数 Shannon-Wiener index | 抽样 Rarefraction (N = 1,000) | Pielou均匀度指数 Pielou evenness index |
---|---|---|---|---|---|
幼苗样方 seedling plots 1 m × 1 m幼苗样方 1 m × 1 m seedling plots | 118 | 4,718 | 4.03 | 84.87 | 0.53 |
5 m × 5 m幼苗样方 5 m × 5 m seedling plots 非幼苗样方 Non-seedling plots | 138 | 20,581 | 4.25 | 89.22 | 0.49 |
1 cm ≤ DBH < 2.5 cm | 144 | 70,916 | 4.11 | 71.83 | 0.42 |
2.5 cm ≤ DBH < 7.5 cm | 132 | 45,524 | 4.05 | 72.23 | 0.43 |
7.5 cm ≤ DBH < 22.5 cm | 115 | 17,835 | 3.81 | 66.70 | 0.42 |
DBH ≥ 22.5 cm | 63 | 6,425 | 2.63 | 35.65 | 0.33 |
图3 古田山24 ha森林样地5 m × 5 m幼苗样方与非幼苗样方的物种多度对比图
Fig. 3 Comparison between the abundance of 5 m × 5 m seedling plots and non-seedling plots in the 24 ha GTS forest dynamics plot
图4 古田山24 ha森林动态监测样地5 m × 5 m幼苗与非幼苗样方物种等级关系图
Fig. 4 Relationship of species rank between 5 m × 5 m seedling plots and non-seedling plots in the 24 ha GTS forest dynamics plot
低地山谷 Low valley | 低地山脊 | 中位山坡 | 高地山脊 | 整个样地 | |
---|---|---|---|---|---|
Low ridge | Middle slope | High ridge | All types | ||
样方数 No. of plots | 127 | 122 | 14 | 22 | 285 |
幼苗数/样方数 No. of seedlings/No. of plots | 83.74 ± 11.80 | 61.21 ± 9.69 | 95.92 ± 16.77 | 51.54 ± 8.03 | 72.21 ± 9.28 |
物种数/样方数 No. of species/No. of plots | 22.22 ± 0.76 | 15.77 ± 0.73 | 24.71 ± 2.06 | 13.54 ± 1.04 | 18.92 ± 0.54 |
Shannon-Wiener指数/样方数 Shannon-Wiener index/ No. of plots | 2.65 ± 0.03 | 2.05 ± 0.05 | 2.59 ± 0.09 | 1.96 ± 0.09 | 2.33 ± 0.33 |
表3 古田山5 m × 5 m幼苗样方不同生境内物种丰富度和多样性
Table 3 Richness and species diversity of seedlings in different habitat types in GTS 5 m × 5 m seedling plots
低地山谷 Low valley | 低地山脊 | 中位山坡 | 高地山脊 | 整个样地 | |
---|---|---|---|---|---|
Low ridge | Middle slope | High ridge | All types | ||
样方数 No. of plots | 127 | 122 | 14 | 22 | 285 |
幼苗数/样方数 No. of seedlings/No. of plots | 83.74 ± 11.80 | 61.21 ± 9.69 | 95.92 ± 16.77 | 51.54 ± 8.03 | 72.21 ± 9.28 |
物种数/样方数 No. of species/No. of plots | 22.22 ± 0.76 | 15.77 ± 0.73 | 24.71 ± 2.06 | 13.54 ± 1.04 | 18.92 ± 0.54 |
Shannon-Wiener指数/样方数 Shannon-Wiener index/ No. of plots | 2.65 ± 0.03 | 2.05 ± 0.05 | 2.59 ± 0.09 | 1.96 ± 0.09 | 2.33 ± 0.33 |
生境类型 | 1 m × 1 m 幼苗样方 | 5 m × 5 m幼苗样方 | 24 ha样地(非幼苗样方) |
---|---|---|---|
Habitat type | 1 m × 1m seedling plots | 5 m × 5 m seedling plots | 24 ha forest dynamics plot (non-seedling plots) |
低地山谷 Low valley | 矩形叶鼠刺 Itea omeiensis | 虎皮楠 Daphniphyllum pentandrum | 浙江新木姜子 Neolitsea aurata var. chekiangensis |
杨梅叶蚊母树 Distylium myricoides | 矩形叶鼠刺 Itea omeiensis | 毛花连蕊茶 Camellia fraterna | |
红楠 Machilus thunbergii | 拟赤杨 Alniphyllum fortunei | – | |
– | 毛花连蕊茶 Camellia fraterna | – | |
– | 野漆树 Toxicodendron succedaneum | – | |
– | 浙江新木姜子 Neolitsea aurata var. chekiangensis | – | |
中位山坡 Middle slope | 细叶青冈 Cyclobalanopsis gracilis | 浙江红花油茶 Camellia chekiangoleosa | – |
红楠 Machilus thunbergii | 灰白蜡瓣花 Corylopsis glandulifera | – | |
– | 马银花 Rhododendron ovatum | – | |
– | 北江荛花 Wikstroemia monnula | – | |
高位山坡 High slope | – | – | 短柄枹 Quercus serrata |
– | – | 毛果南烛 Lyonia ovalifolia var. hebecarpa | |
– | – | 满山红 Rhododendron mariesii | |
高地山脊 High ridge | 木荷 Schima superba | 木荷 Schima superba | 化香 Platycarya strobilacea |
苦枥木 Fraxinus insularis | 美丽胡枝子 Lespedeza thunbergii subsp. formosa | 山橿 Lindera reflexa | |
映山红 Rhododendron simsii | 映山红 Rhododendron simsii | 石灰花楸 Sorbus folgneri | |
山橿 Lindera reflexa | – | 山合欢 Albizia kalkora | |
红楠 Machilus thunbergii | – | – |
表4 古田山24 ha森林样地幼苗与非幼苗生境的指示种
Table 4 The indicator species in seedling and non-seedling plots in the 24 ha GTS forest dynamics plot
生境类型 | 1 m × 1 m 幼苗样方 | 5 m × 5 m幼苗样方 | 24 ha样地(非幼苗样方) |
---|---|---|---|
Habitat type | 1 m × 1m seedling plots | 5 m × 5 m seedling plots | 24 ha forest dynamics plot (non-seedling plots) |
低地山谷 Low valley | 矩形叶鼠刺 Itea omeiensis | 虎皮楠 Daphniphyllum pentandrum | 浙江新木姜子 Neolitsea aurata var. chekiangensis |
杨梅叶蚊母树 Distylium myricoides | 矩形叶鼠刺 Itea omeiensis | 毛花连蕊茶 Camellia fraterna | |
红楠 Machilus thunbergii | 拟赤杨 Alniphyllum fortunei | – | |
– | 毛花连蕊茶 Camellia fraterna | – | |
– | 野漆树 Toxicodendron succedaneum | – | |
– | 浙江新木姜子 Neolitsea aurata var. chekiangensis | – | |
中位山坡 Middle slope | 细叶青冈 Cyclobalanopsis gracilis | 浙江红花油茶 Camellia chekiangoleosa | – |
红楠 Machilus thunbergii | 灰白蜡瓣花 Corylopsis glandulifera | – | |
– | 马银花 Rhododendron ovatum | – | |
– | 北江荛花 Wikstroemia monnula | – | |
高位山坡 High slope | – | – | 短柄枹 Quercus serrata |
– | – | 毛果南烛 Lyonia ovalifolia var. hebecarpa | |
– | – | 满山红 Rhododendron mariesii | |
高地山脊 High ridge | 木荷 Schima superba | 木荷 Schima superba | 化香 Platycarya strobilacea |
苦枥木 Fraxinus insularis | 美丽胡枝子 Lespedeza thunbergii subsp. formosa | 山橿 Lindera reflexa | |
映山红 Rhododendron simsii | 映山红 Rhododendron simsii | 石灰花楸 Sorbus folgneri | |
山橿 Lindera reflexa | – | 山合欢 Albizia kalkora | |
红楠 Machilus thunbergii | – | – |
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