Chin J Plant Ecol ›› 2013, Vol. 37 ›› Issue (6): 542-550.DOI: 10.3724/SP.J.1258.2013.00055
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ZHANG Min1,PAN Yan-Xia2,YANG Hong-Xiao1,*()
Received:
2013-01-04
Accepted:
2013-03-11
Online:
2013-01-04
Published:
2013-06-05
Contact:
YANG Hong-Xiao
ZHANG Min,PAN Yan-Xia,YANG Hong-Xiao. Species abundance patterns of supratidal sandy grassland along China’s Shandong Peninsula and their responses to human disturbances[J]. Chin J Plant Ecol, 2013, 37(6): 542-550.
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URL: https://www.plant-ecology.com/EN/10.3724/SP.J.1258.2013.00055
物种或裸地 Species or bare land | 习性 Habit | 生活型 Life form | 高度 Height (cm) | 寿命 Lifetime (a) | 根型 Root form | 根深 Root depth (cm) | 近原生状态的物种频率 Species frequency in nearly original state (%) | 池塘堤坝的物种频率 Species frequency on pond walls (%) | 旅游践踏状态的物种频率 Species frequency under tourist trampling (%) |
---|---|---|---|---|---|---|---|---|---|
裸地 Bare land | 11.60 | 18.40 | 39.10 | ||||||
沙钻薹草 Carex kobomugi | CP | G | <50 | >2 | F | <50 | 49.41 | 41.96 | 3.33 |
粗毛鸭嘴草 Ischaemum bartatum | CP | G | <50 | >2 | F | <50 | 31.09 | 1.27 | 1.96 |
肾叶打碗花 Calystegia soldanella | CP | G | <50 | >2 | T | <50 | 18.22 | 27.16 | 11.67 |
砂引草 Messerschmidia sibirica | CP | G | <50 | >2 | T | <50 | 13.17 | 2.16 | 7.25 |
拟漆姑 Spergularia marina | CP | G | <50 | <2 | T | <50 | 12.97 | ||
滨麦 Leymus mollis | CP | G | <50 | >2 | F | <50 | 5.84 | 23.33 | |
矮生薹草 Carex pumila | CP | G | <50 | >2 | F | <50 | 3.47 | 6.47 | 13.73 |
沙滩黄芩 Scutellaria strigillosa | CP | G | <50 | >2 | T | <50 | 2.08 | ||
珊瑚菜 Glehnia littoralis | CP | G | <50 | >2 | T | >50 | 1.49 | ||
单叶蔓荆 Vitex trifolia var. simplicifolia | CP | W | <50 | >2 | T | >50 | 0.89 | 7.94 | |
沙苦荬菜 Chorisis repens | CP | G | <50 | >2 | T | <50 | 0.10 | 0.29 | 0.59 |
海滨香豌豆 Lathyrus maritimus | CP | G | <50 | >2 | T | <50 | 1.47 | ||
月见草 Oenothera erythrosepala | NTP | G | <50 | <2 | T | <50 | 2.77 | ||
独行菜 Lepidium apetalum | NTP | G | <50 | <2 | T | <50 | 2.57 | ||
猪毛菜 Salsola collina | NTP | G | <50 | <2 | T | <50 | 1.39 | 4.90 | 2.25 |
白茅 Imperata cylindrica | NTP | G | <50 | >2 | F | <50 | 0.99 | 2.94 | |
小蓬草 Conyza canadensis | NTP | G | >50 | <2 | T | <50 | 0.99 | ||
兴安胡枝子 Lespedeza davurica | NTP | W | <50 | >2 | T | <50 | 0.30 | ||
稗 Echinochloa crusgalli | NTP | G | >50 | <2 | F | <50 | 0.20 | 0.59 | 0.10 |
芦苇 Phragmites australis | NTP | G | >50 | >2 | F | <50 | 0.10 | 0.10 | |
白茎盐生草 Halogeton arachnoideus | NTP | G | <50 | <2 | T | <50 | 0.10 | ||
酸模 Rumex acetosa | NTP | G | >50 | >2 | T | <50 | 0.10 | ||
紫穗槐 Amorpha fruticosa | NTP | W | >50 | >2 | T | >50 | 0.10 | ||
狗牙根 Cynodon dactylon | NTP | G | <50 | >2 | F | <50 | 4.41 | 19.41 | |
香附子 Cyperus rotundus | NTP | G | <50 | >2 | F | <50 | 13.04 | ||
西伯利亚蓼 Polygonum sibiricum | NTP | G | <50 | >2 | T | <50 | 2.16 | ||
盐生草 Halogeton glomeratus | NTP | G | <50 | <2 | T | <50 | 0.69 | 1.37 | |
盐地碱蓬 Suaeda salsa | NTP | G | <50 | <2 | T | <50 | 0.29 | ||
苍耳 Xanthium sibiricum | NTP | G | >50 | <2 | T | <50 | 0.20 | ||
灰绿藜 Chenopodium glaucum | NTP | G | <50 | <2 | T | <50 | 0.20 | ||
酸模叶蓼 Polygonum lapathifolium | NTP | G | >50 | <2 | T | <50 | 0.20 | ||
紫苜蓿 Medicago sativa | NTP | G | >50 | >2 | T | <50 | 0.20 | ||
藜 Chenopodium album | NTP | G | <50 | <2 | T | <50 | 0.10 | 0.10 | |
巴天酸模 Rumex patientia | NTP | G | >50 | >2 | T | <50 | 0.10 | ||
刺沙蓬 Salsola ruthenica | NTP | G | >50 | <2 | T | <50 | 0.10 | ||
虫实 Corispermum spp. | NTP | G | <50 | <2 | T | <50 | 0.88 | ||
马齿苋 Portulaca oleracea | NTP | G | <50 | <2 | T | <50 | 0.10 |
Table 1 Species composition of supratidal sandy grassland in three different conditions
物种或裸地 Species or bare land | 习性 Habit | 生活型 Life form | 高度 Height (cm) | 寿命 Lifetime (a) | 根型 Root form | 根深 Root depth (cm) | 近原生状态的物种频率 Species frequency in nearly original state (%) | 池塘堤坝的物种频率 Species frequency on pond walls (%) | 旅游践踏状态的物种频率 Species frequency under tourist trampling (%) |
---|---|---|---|---|---|---|---|---|---|
裸地 Bare land | 11.60 | 18.40 | 39.10 | ||||||
沙钻薹草 Carex kobomugi | CP | G | <50 | >2 | F | <50 | 49.41 | 41.96 | 3.33 |
粗毛鸭嘴草 Ischaemum bartatum | CP | G | <50 | >2 | F | <50 | 31.09 | 1.27 | 1.96 |
肾叶打碗花 Calystegia soldanella | CP | G | <50 | >2 | T | <50 | 18.22 | 27.16 | 11.67 |
砂引草 Messerschmidia sibirica | CP | G | <50 | >2 | T | <50 | 13.17 | 2.16 | 7.25 |
拟漆姑 Spergularia marina | CP | G | <50 | <2 | T | <50 | 12.97 | ||
滨麦 Leymus mollis | CP | G | <50 | >2 | F | <50 | 5.84 | 23.33 | |
矮生薹草 Carex pumila | CP | G | <50 | >2 | F | <50 | 3.47 | 6.47 | 13.73 |
沙滩黄芩 Scutellaria strigillosa | CP | G | <50 | >2 | T | <50 | 2.08 | ||
珊瑚菜 Glehnia littoralis | CP | G | <50 | >2 | T | >50 | 1.49 | ||
单叶蔓荆 Vitex trifolia var. simplicifolia | CP | W | <50 | >2 | T | >50 | 0.89 | 7.94 | |
沙苦荬菜 Chorisis repens | CP | G | <50 | >2 | T | <50 | 0.10 | 0.29 | 0.59 |
海滨香豌豆 Lathyrus maritimus | CP | G | <50 | >2 | T | <50 | 1.47 | ||
月见草 Oenothera erythrosepala | NTP | G | <50 | <2 | T | <50 | 2.77 | ||
独行菜 Lepidium apetalum | NTP | G | <50 | <2 | T | <50 | 2.57 | ||
猪毛菜 Salsola collina | NTP | G | <50 | <2 | T | <50 | 1.39 | 4.90 | 2.25 |
白茅 Imperata cylindrica | NTP | G | <50 | >2 | F | <50 | 0.99 | 2.94 | |
小蓬草 Conyza canadensis | NTP | G | >50 | <2 | T | <50 | 0.99 | ||
兴安胡枝子 Lespedeza davurica | NTP | W | <50 | >2 | T | <50 | 0.30 | ||
稗 Echinochloa crusgalli | NTP | G | >50 | <2 | F | <50 | 0.20 | 0.59 | 0.10 |
芦苇 Phragmites australis | NTP | G | >50 | >2 | F | <50 | 0.10 | 0.10 | |
白茎盐生草 Halogeton arachnoideus | NTP | G | <50 | <2 | T | <50 | 0.10 | ||
酸模 Rumex acetosa | NTP | G | >50 | >2 | T | <50 | 0.10 | ||
紫穗槐 Amorpha fruticosa | NTP | W | >50 | >2 | T | >50 | 0.10 | ||
狗牙根 Cynodon dactylon | NTP | G | <50 | >2 | F | <50 | 4.41 | 19.41 | |
香附子 Cyperus rotundus | NTP | G | <50 | >2 | F | <50 | 13.04 | ||
西伯利亚蓼 Polygonum sibiricum | NTP | G | <50 | >2 | T | <50 | 2.16 | ||
盐生草 Halogeton glomeratus | NTP | G | <50 | <2 | T | <50 | 0.69 | 1.37 | |
盐地碱蓬 Suaeda salsa | NTP | G | <50 | <2 | T | <50 | 0.29 | ||
苍耳 Xanthium sibiricum | NTP | G | >50 | <2 | T | <50 | 0.20 | ||
灰绿藜 Chenopodium glaucum | NTP | G | <50 | <2 | T | <50 | 0.20 | ||
酸模叶蓼 Polygonum lapathifolium | NTP | G | >50 | <2 | T | <50 | 0.20 | ||
紫苜蓿 Medicago sativa | NTP | G | >50 | >2 | T | <50 | 0.20 | ||
藜 Chenopodium album | NTP | G | <50 | <2 | T | <50 | 0.10 | 0.10 | |
巴天酸模 Rumex patientia | NTP | G | >50 | >2 | T | <50 | 0.10 | ||
刺沙蓬 Salsola ruthenica | NTP | G | >50 | <2 | T | <50 | 0.10 | ||
虫实 Corispermum spp. | NTP | G | <50 | <2 | T | <50 | 0.88 | ||
马齿苋 Portulaca oleracea | NTP | G | <50 | <2 | T | <50 | 0.10 |
模型 Model | 真实值与理论值比较 Comparison of real data with theoretical data | 近原生状态 Nearly original state | 池塘堤坝 Pond walls | 旅游条件 Tourist trampling |
---|---|---|---|---|
中性理论模型 Neutral theoretical model | 相对偏差 Relative deviation | 30.9% | 25.2% | 37.7% |
K-S检验显著性 K-S test significance | 0.871 | 1.000 | 0.632 | |
Pearson相关系数 Pearson correlation coefficient | 0.995 | 0.982 | 0.943 | |
AIC值 Aikake’s information criterion | 115.88 | 106.16 | 141.26 | |
几何级数模型 Geometric-series model | 相对偏差 Relative deviation | 34.3% | 31.9% | 45.2% |
K-S检验显著性 K-S test significance | 0.632 | 1.000 | 0.872 | |
Pearson相关系数 Pearson correlation coefficient | 0.980 | 0.956 | 0.864 | |
AIC值 Aikake’s information criterion | 154.04 | 123.69 | 157.94 | |
分割线段模型 Broken stick model | 相对偏差 Relative deviation | 71.0% | 64.7% | 65.7% |
K-S检验显著性 K-S test significance | 0.109 | 0.215 | 0.049 | |
Pearson相关系数 Pearson correlation coefficient | 0.943 | 0.957 | 0.963 | |
AIC值 Aikake’s information criterion | 184.13 | 129.63 | 140.87 | |
重叠生态位模型 Overlapping niche model | 相对偏差 Relative deviation | 85.8% | 77.0% | 76.0% |
K-S检验显著性 K-S test significance | 0.020 | 0.093 | 0.049 | |
Pearson相关系数 Pearson correlation coefficient | 0.827 | 0.874 | 0.898 | |
AIC值 Aikake’s information criterion | 196.44 | 139.99 | 156.35 |
Table 2 Fitting effects of four theoretical models
模型 Model | 真实值与理论值比较 Comparison of real data with theoretical data | 近原生状态 Nearly original state | 池塘堤坝 Pond walls | 旅游条件 Tourist trampling |
---|---|---|---|---|
中性理论模型 Neutral theoretical model | 相对偏差 Relative deviation | 30.9% | 25.2% | 37.7% |
K-S检验显著性 K-S test significance | 0.871 | 1.000 | 0.632 | |
Pearson相关系数 Pearson correlation coefficient | 0.995 | 0.982 | 0.943 | |
AIC值 Aikake’s information criterion | 115.88 | 106.16 | 141.26 | |
几何级数模型 Geometric-series model | 相对偏差 Relative deviation | 34.3% | 31.9% | 45.2% |
K-S检验显著性 K-S test significance | 0.632 | 1.000 | 0.872 | |
Pearson相关系数 Pearson correlation coefficient | 0.980 | 0.956 | 0.864 | |
AIC值 Aikake’s information criterion | 154.04 | 123.69 | 157.94 | |
分割线段模型 Broken stick model | 相对偏差 Relative deviation | 71.0% | 64.7% | 65.7% |
K-S检验显著性 K-S test significance | 0.109 | 0.215 | 0.049 | |
Pearson相关系数 Pearson correlation coefficient | 0.943 | 0.957 | 0.963 | |
AIC值 Aikake’s information criterion | 184.13 | 129.63 | 140.87 | |
重叠生态位模型 Overlapping niche model | 相对偏差 Relative deviation | 85.8% | 77.0% | 76.0% |
K-S检验显著性 K-S test significance | 0.020 | 0.093 | 0.049 | |
Pearson相关系数 Pearson correlation coefficient | 0.827 | 0.874 | 0.898 | |
AIC值 Aikake’s information criterion | 196.44 | 139.99 | 156.35 |
Fig. 1 Species-abundance patterns of supratidal sandy grassland. The horizontal axis refers to ranks of species in their more-to-less sorting. A, Supratidal sandy grassland in nearly original state in Jiaonan. B, Supratidal sandy grassland on pond walls in Muping. C, Supratidal sandy grassland suffering from tourist trampling in Penglai.
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