Ecology and Environment ›› 2023, Vol. 32 ›› Issue (1): 26-35.DOI: 10.16258/j.cnki.1674-5906.2023.01.004
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ZHANG Lijin1,2,3,4(), DU Hu1,2,4, ZENG Fuping1,2,4, HUANG Guoqin3, SONG Min5, SONG Tongqing1,2,4,*(
)
Received:
2022-06-24
Online:
2023-01-18
Published:
2023-04-06
Contact:
SONG Tongqing
张立进1,2,3,4(), 杜虎1,2,4, 曾馥平1,2,4, 黄国勤3, 宋敏5, 宋同清1,2,4,*(
)
通讯作者:
宋同清
作者简介:
张立进(1990年生),博士研究生,研究方向为植物生态学、农业生态学。E-mail: 570208044@qq.com
基金资助:
CLC Number:
ZHANG Lijin, DU Hu, ZENG Fuping, HUANG Guoqin, SONG Min, SONG Tongqing. Discussion on the Relationship between Productivity and Diversity during Vegetation Restoration in the Karst Peak-cluster Depression[J]. Ecology and Environment, 2023, 32(1): 26-35.
张立进, 杜虎, 曾馥平, 黄国勤, 宋敏, 宋同清. 喀斯特峰丛洼地植被恢复过程中生产力与多样性关系探讨[J]. 生态环境学报, 2023, 32(1): 26-35.
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URL: https://www.jeesci.com/EN/10.16258/j.cnki.1674-5906.2023.01.004
植被 类型 | 物种 | 重要值 (IV) | 物种、生产力变化 | |||
---|---|---|---|---|---|---|
2007(IV) | 2017(IV) | 物种数量变化 | 生产力变化/(Mg·hm-2·a-1) | |||
灌木林 | 黄荆 Vitex negundo | 29.81 | 27.61 | -1512 | -0.056 | |
八角枫 Alangium chinense | 12.62 | 12.2 | -205 | -0.107 | ||
小叶女贞 Ligustrum japonicum | 4.98 | 7.51 | -106 | 0.022 | ||
野桐 Mallotus japonicus | 4.36 | 4.24 | -70 | -0.01 | ||
小巴豆 Croton tiglium | 4.24 | 4.16 | -62 | 0.016 | ||
石山楠 Phoebe calcarea | 2.88 | 2.62 | -23 | -0.021 | ||
盐肤木 Rhus chinensis | 2.77 | 1.62 | -69 | -0.019 | ||
三桠苦 Evodia lepta | 2.75 | 1.92 | -59 | -0.016 | ||
火棘 Pyracantha fortuneana | 2.02 | 0 | -88 | -0.008 | ||
红背山麻秆 Alchornea trewioides | 1.9 | 1.31 | -47 | -0.004 | ||
次生林 | 菜豆树 Radermachera sinica | 15.63 | 10.71 | -51 | 0.09 | |
灰毛浆果楝 Cipadessa cinerascens | 11.46 | 11.4 | -154 | 0.168 | ||
香椿 Toona sinensis | 10.74 | 10.57 | -5 | 0.239 | ||
刀果鞍叶羊蹄甲 Bauhinia brachycarpa | 8.1 | 12.75 | 45 | 0.308 | ||
盐肤木 Rhus chinensis | 3.56 | 2.73 | -46 | 0.005 | ||
板栗 Castanea mollissima | 3.32 | 3.24 | -107 | 0.119 | ||
长管越南茜 Rubovietnamia aristata | 2.6 | 2.99 | -2 | 0.028 | ||
斜叶榕 Ficus tinctoria | 2.51 | 2.59 | -13 | 0.019 | ||
任豆 Zenia insignis | 2.43 | 3.55 | -5 | 0.155 | ||
杜茎山 Maesa japonica | 2.31 | 1.28 | -38 | -0.004 | ||
原生林 | 铁榄 Sinosideroxylon pedunculatum | 6.8 | 5.74 | -149 | 1.043 | |
小叶女贞 Ligustrum japonicum | 5.32 | 3.62 | -130 | 0.584 | ||
掌叶木 Handeliodendron bodinieri | 4.56 | 4.74 | -11 | 0.229 | ||
菜豆树 Radermachera sinica | 4.04 | 3.78 | -33 | 0.547 | ||
粗糠柴 Mallotus philippensis | 9.97 | 4.78 | -132 | 0.196 | ||
小叶栾树 Boniodendron minus | 9.89 | 1.98 | 3 | 0.59 | ||
杜茎山 Maesa japonica | 3.67 | 4.12 | -149 | 0.614 | ||
杉树 Cunninghamia lanceolata | 3.15 | 3.31 | -6 | 0.206 | ||
白毛长叶紫珠 Callicarpa longifolia | 2.41 | 3.32 | -23 | 0.655 | ||
枫香树 Liquidambar formosana | 2.25 | 3.19 | -8 | 0.415 |
Table 1 Changes of main characteristic values of three vegetation types in 2007-2017
植被 类型 | 物种 | 重要值 (IV) | 物种、生产力变化 | |||
---|---|---|---|---|---|---|
2007(IV) | 2017(IV) | 物种数量变化 | 生产力变化/(Mg·hm-2·a-1) | |||
灌木林 | 黄荆 Vitex negundo | 29.81 | 27.61 | -1512 | -0.056 | |
八角枫 Alangium chinense | 12.62 | 12.2 | -205 | -0.107 | ||
小叶女贞 Ligustrum japonicum | 4.98 | 7.51 | -106 | 0.022 | ||
野桐 Mallotus japonicus | 4.36 | 4.24 | -70 | -0.01 | ||
小巴豆 Croton tiglium | 4.24 | 4.16 | -62 | 0.016 | ||
石山楠 Phoebe calcarea | 2.88 | 2.62 | -23 | -0.021 | ||
盐肤木 Rhus chinensis | 2.77 | 1.62 | -69 | -0.019 | ||
三桠苦 Evodia lepta | 2.75 | 1.92 | -59 | -0.016 | ||
火棘 Pyracantha fortuneana | 2.02 | 0 | -88 | -0.008 | ||
红背山麻秆 Alchornea trewioides | 1.9 | 1.31 | -47 | -0.004 | ||
次生林 | 菜豆树 Radermachera sinica | 15.63 | 10.71 | -51 | 0.09 | |
灰毛浆果楝 Cipadessa cinerascens | 11.46 | 11.4 | -154 | 0.168 | ||
香椿 Toona sinensis | 10.74 | 10.57 | -5 | 0.239 | ||
刀果鞍叶羊蹄甲 Bauhinia brachycarpa | 8.1 | 12.75 | 45 | 0.308 | ||
盐肤木 Rhus chinensis | 3.56 | 2.73 | -46 | 0.005 | ||
板栗 Castanea mollissima | 3.32 | 3.24 | -107 | 0.119 | ||
长管越南茜 Rubovietnamia aristata | 2.6 | 2.99 | -2 | 0.028 | ||
斜叶榕 Ficus tinctoria | 2.51 | 2.59 | -13 | 0.019 | ||
任豆 Zenia insignis | 2.43 | 3.55 | -5 | 0.155 | ||
杜茎山 Maesa japonica | 2.31 | 1.28 | -38 | -0.004 | ||
原生林 | 铁榄 Sinosideroxylon pedunculatum | 6.8 | 5.74 | -149 | 1.043 | |
小叶女贞 Ligustrum japonicum | 5.32 | 3.62 | -130 | 0.584 | ||
掌叶木 Handeliodendron bodinieri | 4.56 | 4.74 | -11 | 0.229 | ||
菜豆树 Radermachera sinica | 4.04 | 3.78 | -33 | 0.547 | ||
粗糠柴 Mallotus philippensis | 9.97 | 4.78 | -132 | 0.196 | ||
小叶栾树 Boniodendron minus | 9.89 | 1.98 | 3 | 0.59 | ||
杜茎山 Maesa japonica | 3.67 | 4.12 | -149 | 0.614 | ||
杉树 Cunninghamia lanceolata | 3.15 | 3.31 | -6 | 0.206 | ||
白毛长叶紫珠 Callicarpa longifolia | 2.41 | 3.32 | -23 | 0.655 | ||
枫香树 Liquidambar formosana | 2.25 | 3.19 | -8 | 0.415 |
森林类型 | 变量 | 样本数n | 线性模型 | 二次模型 | 模式 | |||
---|---|---|---|---|---|---|---|---|
R2 | P | R2 | P | |||||
灌木林 | 物种香浓指数 | 77 | 0.342 | <0.001 | 0.512 | <0.001 | 二次项曲线 ( | |
物种辛普森指数 | 75 | 0.022 | 0.260 | 0.030 | 0.244 | 负线性和二次项曲线 ( | ||
物种均匀度 | 77 | 0.077 | 0.035 | 0.081 | 0.029 | 负线性 ( | ||
次生林 | 物种香浓指数 | 67 | 0.059 | 0.049 | 0.061 | 0.042 | 正线性 ( | |
物种辛普森指数 | 66 | 0.076 | 0.026 | 0.077 | 0.026 | 正线性 ( | ||
物种均匀度 | 67 | 0.008 | 0.489 | 0.032 | 0.135 | 二次项曲线 ( | ||
原生林 | 物种香浓指数 | 61 | 0.001 | 0.782 | 0.001 | 0.786 | ns ( | |
物种辛普森指数 | 62 | <0.001 | 0.873 | 0.031 | 0.254 | 二次项曲线 ( | ||
物种均匀度 | 62 | 0.006 | 0.492 | 0.047 | 0.196 | 二次 ( |
Table 2 Linear and quadratic regression analysis between species diversity and productivity of three types of vegetation
森林类型 | 变量 | 样本数n | 线性模型 | 二次模型 | 模式 | |||
---|---|---|---|---|---|---|---|---|
R2 | P | R2 | P | |||||
灌木林 | 物种香浓指数 | 77 | 0.342 | <0.001 | 0.512 | <0.001 | 二次项曲线 ( | |
物种辛普森指数 | 75 | 0.022 | 0.260 | 0.030 | 0.244 | 负线性和二次项曲线 ( | ||
物种均匀度 | 77 | 0.077 | 0.035 | 0.081 | 0.029 | 负线性 ( | ||
次生林 | 物种香浓指数 | 67 | 0.059 | 0.049 | 0.061 | 0.042 | 正线性 ( | |
物种辛普森指数 | 66 | 0.076 | 0.026 | 0.077 | 0.026 | 正线性 ( | ||
物种均匀度 | 67 | 0.008 | 0.489 | 0.032 | 0.135 | 二次项曲线 ( | ||
原生林 | 物种香浓指数 | 61 | 0.001 | 0.782 | 0.001 | 0.786 | ns ( | |
物种辛普森指数 | 62 | <0.001 | 0.873 | 0.031 | 0.254 | 二次项曲线 ( | ||
物种均匀度 | 62 | 0.006 | 0.492 | 0.047 | 0.196 | 二次 ( |
森林类型 | 变量 | 样本数n | 线性模型 | 二次模型 | 模式 | |||
---|---|---|---|---|---|---|---|---|
R2 | P | R2 | P | |||||
灌木林 | 胸径香浓指数 | 62 | 0.248 | <0.001 | 0.248 | <0.001 | 正线性 ( | |
胸径辛普森指数 | 65 | 0.105 | 0.009 | 0.145 | 0.008 | 二次项曲线 ( | ||
胸径均匀度 | 76 | 0.004 | 0.085 | 0.059 | 0.111 | 二次项曲线 ( | ||
林分密度 | 77 | 0.036 | 0.143 | 0.051 | 0.127 | 正线性 ( | ||
次生林 | 胸径香浓指数 | 71 | 0.015 | 0.309 | 0.034 | 0.315 | 二次项曲线 ( | |
胸径辛普森指数 | 73 | 0.002 | 0.718 | 0.003 | 0.893 | ns ( | ||
胸径均匀度 | 73 | 0.003 | 0.145 | 0.320 | 0.135 | 正线性 ( | ||
林分密度 | 69 | 0.062 | 0.040 | 0.088 | 0.031 | 正线性和二次项曲线 ( | ||
原生林 | 胸径香浓指数 | 61 | 0.035 | 0.130 | 0.076 | 0.008 | 二次项曲线 ( | |
胸径辛普森指数 | 62 | 0.001 | 0.785 | 0.027 | 0.405 | ns ( | ||
胸径均匀度 | 62 | 0.033 | 0.140 | 0.062 | 0.131 | 二次项曲线 ( | ||
林分密度 | 62 | <0.001 | 0.905 | 0.012 | 0.658 | ns ( |
Table 3 Linear and quadratic regression analysis between structural diversity and productivity of three types of vegetation
森林类型 | 变量 | 样本数n | 线性模型 | 二次模型 | 模式 | |||
---|---|---|---|---|---|---|---|---|
R2 | P | R2 | P | |||||
灌木林 | 胸径香浓指数 | 62 | 0.248 | <0.001 | 0.248 | <0.001 | 正线性 ( | |
胸径辛普森指数 | 65 | 0.105 | 0.009 | 0.145 | 0.008 | 二次项曲线 ( | ||
胸径均匀度 | 76 | 0.004 | 0.085 | 0.059 | 0.111 | 二次项曲线 ( | ||
林分密度 | 77 | 0.036 | 0.143 | 0.051 | 0.127 | 正线性 ( | ||
次生林 | 胸径香浓指数 | 71 | 0.015 | 0.309 | 0.034 | 0.315 | 二次项曲线 ( | |
胸径辛普森指数 | 73 | 0.002 | 0.718 | 0.003 | 0.893 | ns ( | ||
胸径均匀度 | 73 | 0.003 | 0.145 | 0.320 | 0.135 | 正线性 ( | ||
林分密度 | 69 | 0.062 | 0.040 | 0.088 | 0.031 | 正线性和二次项曲线 ( | ||
原生林 | 胸径香浓指数 | 61 | 0.035 | 0.130 | 0.076 | 0.008 | 二次项曲线 ( | |
胸径辛普森指数 | 62 | 0.001 | 0.785 | 0.027 | 0.405 | ns ( | ||
胸径均匀度 | 62 | 0.033 | 0.140 | 0.062 | 0.131 | 二次项曲线 ( | ||
林分密度 | 62 | <0.001 | 0.905 | 0.012 | 0.658 | ns ( |
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