植物生态学报 ›› 2012, Vol. 36 ›› Issue (2): 117-125.DOI: 10.3724/SP.J.1258.2012.00117 cstr: 32100.14.SP.J.1258.2012.00117
收稿日期:2011-06-02
接受日期:2011-12-10
出版日期:2012-06-02
发布日期:2012-02-22
作者简介:* E-mail: zyd@caf.ac.cn
ZHANG Yuan-Dong*(
), LIU Yan-Chun, LIU Shi-Rong, ZHANG Xiao-He
Received:2011-06-02
Accepted:2011-12-10
Online:2012-06-02
Published:2012-02-22
摘要:
基于树木年轮学与标准地调查法, 研究了川西亚高山林区3种恢复森林类型生物量、蓄积量及生产力动态变化特征, 旨在尝试年轮学在森林生长过程反演中的运用, 并探索不同恢复模式下森林生物量和蓄积量的动态变化。结果表明, 不同恢复类型发育至20年以后, 均进入生长加速期, 平均胸径间差异逐渐显著, 人工云杉(Picea asperata)林胸径增长最快, 明显高于天然恢复的次生桦木(Betula spp.)林和次生针阔混交林。在恢复过程中, 次生针阔混交林一直保持最高的林分平均地上生物量与林分蓄积量, 其地上平均生物量一直显著高于人工云杉林(p < 0.05), 在20年以后显著高于次生桦木林(p < 0.05)。与人工云杉林相比, 次生桦木林在25年前具有相对较高的生物量, 而在25年之后则低于人工云杉林。在0-20年桦木林林分蓄积量略高于云杉林, 而20年以后, 云杉林蓄积量则超过桦木林。不同恢复类型的生产力大小对比显示, 30年之前, 次生针阔混交林>次生桦木林>人工云杉林, 30年之后, 针阔混交林生产力仍然最高, 而人工云杉林则超过次生桦木林。川西林区次生针阔混交林恢复模式在生物量和蓄积量积累方面均具有显著优势。
张远东, 刘彦春, 刘世荣, 张笑鹤. 基于年轮分析的不同恢复途径下森林乔木层生物量和蓄积量的动态变化. 植物生态学报, 2012, 36(2): 117-125. DOI: 10.3724/SP.J.1258.2012.00117
ZHANG Yuan-Dong, LIU Yan-Chun, LIU Shi-Rong, ZHANG Xiao-He. Dynamics of stand biomass and volume of the tree layer in forests with different restoration approaches based on tree-ring analysis. Chinese Journal of Plant Ecology, 2012, 36(2): 117-125. DOI: 10.3724/SP.J.1258.2012.00117
| 森林类型 Forest type | 海拔 Elevation (m) | 坡向 Slope aspect (°) | 坡度 Slope gradient (°) | 林分密度 Stand density (tree · hm-2) | 平均胸径 Mean DBH (cm) | 林龄 Stand age (a) | 样芯数 No. of cores |
|---|---|---|---|---|---|---|---|
| PSFI | 3 212 | NE 40 | 10 | 829.3 | 21.4 ± 6.2 | 43 | 47 |
| PSFII | 3 261 | NE 45 | 15 | 914.5 | 20.1 ± 5.7 | 44 | 49 |
| PSFIII | 3 252 | SE 70 | 10 | 964.7 | 19.7 ± 5.6 | 39 | 53 |
| SBFI | 3 214 | NW 40 | 26 | 3 021.5 | 9.3 ± 3.4 | 49 | 104 |
| SBFII | 3 238 | NW 25 | 20 | 3 086.1 | 11.2 ± 3.3 | 45 | 77 |
| SBFIII | 3 326 | NE 20 | 18 | 2 788.1 | 10.1 ± 4.5 | 50 | 94 |
| SMFI | 3 020 | NE 40 | 30 | 3 262.0 | 11.1 ± 3.4 | 36 | 93 |
| SMFII | 2 990 | NE 20 | 20 | 3 188.1 | 9.5 ± 3.4 | 35 | 124 |
| SMFIII | 3 345 | NE 15 | 20 | 3 032.7 | 11.7 ± 4.6 | 38 | 101 |
表1 川西亚高山地区调查样地的基本情况
Table 1 Basic information of sample plots of subalpine region in Western Sichuan
| 森林类型 Forest type | 海拔 Elevation (m) | 坡向 Slope aspect (°) | 坡度 Slope gradient (°) | 林分密度 Stand density (tree · hm-2) | 平均胸径 Mean DBH (cm) | 林龄 Stand age (a) | 样芯数 No. of cores |
|---|---|---|---|---|---|---|---|
| PSFI | 3 212 | NE 40 | 10 | 829.3 | 21.4 ± 6.2 | 43 | 47 |
| PSFII | 3 261 | NE 45 | 15 | 914.5 | 20.1 ± 5.7 | 44 | 49 |
| PSFIII | 3 252 | SE 70 | 10 | 964.7 | 19.7 ± 5.6 | 39 | 53 |
| SBFI | 3 214 | NW 40 | 26 | 3 021.5 | 9.3 ± 3.4 | 49 | 104 |
| SBFII | 3 238 | NW 25 | 20 | 3 086.1 | 11.2 ± 3.3 | 45 | 77 |
| SBFIII | 3 326 | NE 20 | 18 | 2 788.1 | 10.1 ± 4.5 | 50 | 94 |
| SMFI | 3 020 | NE 40 | 30 | 3 262.0 | 11.1 ± 3.4 | 36 | 93 |
| SMFII | 2 990 | NE 20 | 20 | 3 188.1 | 9.5 ± 3.4 | 35 | 124 |
| SMFIII | 3 345 | NE 15 | 20 | 3 032.7 | 11.7 ± 4.6 | 38 | 101 |
| 树种 Tree species | 地上部分器官 Aboveground organ | 异速生长模型 Allometric model | 决定系数 Determination coefficient | 文献来源 Origin of references | |
|---|---|---|---|---|---|
| 冷杉 Abies spp. | 干 Stem | W = 0.0139(D2H)1.0075 | R2 = 0.998 6 | Luo et al., 2002 | |
| 枝 Branch | W = 0.0014(D2H)1.0503 | R2 = 0.911 8 | |||
| 叶 Leaf | 胸径 DBH < 40 cm时, | W = 0.0003(D2H)1.2032 | R2 = 0.934 1 | ||
| 胸径 DBH > 40 cm时, | W = 11.5060ln(D2H) - 74.7330 | R2 = 0.753 9 | |||
| 云杉 Picea spp. | 干 Stem | W = 0.0405D2.5680 | R2 = 0.989 0 | Luo et al., 2002 | |
| 枝 Branch | W = 0.0037D2.7386 | R2 = 0.945 0 | |||
| 叶 Leaf | 胸径 DBH < 40 cm时, | W = 0.0014D2.9302 | R2 = 0.941 9 | ||
| 胸径 DBH > 40 cm时, | W = 29.5410lnD - 63.1500 | R2 = 0.757 4 | |||
| 桦木 Betula spp. | 干 Stem | W = 0.1411(D2H)0.7234 | R2 = 0.980 1 | Feng et al., 1999 | |
| 枝 Branch | W = 0.0072(D2H)1.0225 | R2 = 0.774 4 | |||
| 叶 Leaf | W = 0.0151(D2H)0.8085 | R2 = 0.828 1 | |||
| 树种 Tree species | 地上部分器官 Aboveground organ | 异速生长模型 Allometric model | 决定系数 Determination coefficient | 文献来源 Origin of references | |
| 槭树 Acer spp. | 干 Stem | W = 0.3274(D2H)0.7218 | R2 = 0.932 5 | Chen, 1983 | |
| 枝 Branch | W = 0.0135(D2H)0.7198 | R2 = 0.911 4 | |||
| 叶 Leaf | W = 0.0235(D2H)0.6929 | R2 = 0.891 7 | |||
| 杨木 Poplar spp. | 干 Stem | W = 0.0537(D2H)0.9270 | R2 = 0.987 0 | Zhu et al., 1988 | |
| 枝 Branch | W = 0.0125(D2H)0.9504 | R2 = 0.863 0 | |||
| 叶 Leaf | W = 0.0221(D2H)0.7583 | R2 = 0.786 0 | |||
| 其他阔叶树 Other broadleaf species | 干 Stem | W = 0.0097(D2H) + 5.8252 | R2 = 0.991 4 | Luo et al., 2002 | |
| 枝 Branch | W = 0.0510(D2H) + 3.5080 | R2 = 0.982 5 | |||
| 叶 Leaf | W = 0.0004(D2H) + 0.7563 | R2 = 0.933 3 | |||
附表I 川西亚高山次生林乔木地上生物量异速生长模型
Appendix I Allometric models for tree aboveground biomass in subalpine secondary forest in Western Sichuan
| 树种 Tree species | 地上部分器官 Aboveground organ | 异速生长模型 Allometric model | 决定系数 Determination coefficient | 文献来源 Origin of references | |
|---|---|---|---|---|---|
| 冷杉 Abies spp. | 干 Stem | W = 0.0139(D2H)1.0075 | R2 = 0.998 6 | Luo et al., 2002 | |
| 枝 Branch | W = 0.0014(D2H)1.0503 | R2 = 0.911 8 | |||
| 叶 Leaf | 胸径 DBH < 40 cm时, | W = 0.0003(D2H)1.2032 | R2 = 0.934 1 | ||
| 胸径 DBH > 40 cm时, | W = 11.5060ln(D2H) - 74.7330 | R2 = 0.753 9 | |||
| 云杉 Picea spp. | 干 Stem | W = 0.0405D2.5680 | R2 = 0.989 0 | Luo et al., 2002 | |
| 枝 Branch | W = 0.0037D2.7386 | R2 = 0.945 0 | |||
| 叶 Leaf | 胸径 DBH < 40 cm时, | W = 0.0014D2.9302 | R2 = 0.941 9 | ||
| 胸径 DBH > 40 cm时, | W = 29.5410lnD - 63.1500 | R2 = 0.757 4 | |||
| 桦木 Betula spp. | 干 Stem | W = 0.1411(D2H)0.7234 | R2 = 0.980 1 | Feng et al., 1999 | |
| 枝 Branch | W = 0.0072(D2H)1.0225 | R2 = 0.774 4 | |||
| 叶 Leaf | W = 0.0151(D2H)0.8085 | R2 = 0.828 1 | |||
| 树种 Tree species | 地上部分器官 Aboveground organ | 异速生长模型 Allometric model | 决定系数 Determination coefficient | 文献来源 Origin of references | |
| 槭树 Acer spp. | 干 Stem | W = 0.3274(D2H)0.7218 | R2 = 0.932 5 | Chen, 1983 | |
| 枝 Branch | W = 0.0135(D2H)0.7198 | R2 = 0.911 4 | |||
| 叶 Leaf | W = 0.0235(D2H)0.6929 | R2 = 0.891 7 | |||
| 杨木 Poplar spp. | 干 Stem | W = 0.0537(D2H)0.9270 | R2 = 0.987 0 | Zhu et al., 1988 | |
| 枝 Branch | W = 0.0125(D2H)0.9504 | R2 = 0.863 0 | |||
| 叶 Leaf | W = 0.0221(D2H)0.7583 | R2 = 0.786 0 | |||
| 其他阔叶树 Other broadleaf species | 干 Stem | W = 0.0097(D2H) + 5.8252 | R2 = 0.991 4 | Luo et al., 2002 | |
| 枝 Branch | W = 0.0510(D2H) + 3.5080 | R2 = 0.982 5 | |||
| 叶 Leaf | W = 0.0004(D2H) + 0.7563 | R2 = 0.933 3 | |||
| 树种 Tree species | 材积公式 Volume equation (m3) |
|---|---|
| 桦木 Betula spp. | $V = 0.00004894 \times {\left( {0.9839 \times D - 0.3303} \right)^{2.0173}} \times {\left( {\frac{{33.2727 - 1031.4484}}{{31.549 + D}}} \right)^{0.9388}}$ |
| 冷杉 Abies spp. | $V = 0.00006322 \times {\left( { - 0.1027 + 0.99576 \times D} \right)^{1.901}} \times {\left( {\frac{{45.79737 - 1837.226}}{{D + 38.40604}}} \right)^{0.963}}$ |
| 云杉 Picea spp. | $V = 0.00005679 \times {\left( {0.37388 + 0.9721 \times D} \right)^{1.852}} \times {\left( {\frac{D}{{1.129 + 0.0161 \times D}}} \right)^{1.0335}}$ |
| 杨树 Poplar spp. | $V = 0.00005275 \times {\left( { - 0.5162 + 1.0942 \times D} \right)^{1.94526}} \times {\left( {\frac{D}{{0.74623 + 0.0421 \times D}}} \right)^{0.93885}}$ |
| 槭树 Acer spp. | $V = 0.00005275 \times {\left( {0.49896 + 0.9661 \times D} \right)^{1.945}} \times {\left( {\frac{D}{{0.84118 + 0.0381}}} \right)^{0.93885}}$ |
附表II 川西主要树种一元立木材积表1)
Appendix II Table of one-way tree volume models of the main tree species in Western Sichuan1)
| 树种 Tree species | 材积公式 Volume equation (m3) |
|---|---|
| 桦木 Betula spp. | $V = 0.00004894 \times {\left( {0.9839 \times D - 0.3303} \right)^{2.0173}} \times {\left( {\frac{{33.2727 - 1031.4484}}{{31.549 + D}}} \right)^{0.9388}}$ |
| 冷杉 Abies spp. | $V = 0.00006322 \times {\left( { - 0.1027 + 0.99576 \times D} \right)^{1.901}} \times {\left( {\frac{{45.79737 - 1837.226}}{{D + 38.40604}}} \right)^{0.963}}$ |
| 云杉 Picea spp. | $V = 0.00005679 \times {\left( {0.37388 + 0.9721 \times D} \right)^{1.852}} \times {\left( {\frac{D}{{1.129 + 0.0161 \times D}}} \right)^{1.0335}}$ |
| 杨树 Poplar spp. | $V = 0.00005275 \times {\left( { - 0.5162 + 1.0942 \times D} \right)^{1.94526}} \times {\left( {\frac{D}{{0.74623 + 0.0421 \times D}}} \right)^{0.93885}}$ |
| 槭树 Acer spp. | $V = 0.00005275 \times {\left( {0.49896 + 0.9661 \times D} \right)^{1.945}} \times {\left( {\frac{D}{{0.84118 + 0.0381}}} \right)^{0.93885}}$ |
图1 三种恢复森林类型不同径级的年平均生长率(平均值±标准误差)。PSF, 人工云杉林; SBF, 次生桦木林; SMF, 次生针阔混交林。同一森林类型内标相同小写字母者表示径级间差异不显著(p > 0.05)。
Fig. 1 Annual mean growth rate of different DBH classes for three recovery forest types (mean ± SE). DBH, diameter at breast height. PSF, planted spruce (Picea asperata) forest; SBF, secondary birch (Betula spp.) forest; SMF, secondary coniferous and broad-leaved mixed forest. Values labelled by the same lowercase in each forest type are not significant different between diameter classes (p > 0.05).
图2 三种恢复森林类型林分平均胸径随林龄的变化。PSF, 人工云杉林; SBF, 次生桦木林; SMF, 次生针阔混交林。小图为0-15年平均胸径的放大图。
Fig. 2 Changes of stand mean diameter at breast height (DBH) with stand age for three recovery forest types. PSF, planted spruce (Picea asperata) forest; SBF, secondary birch (Betula spp.) forest; SMF, secondary coniferous and broad- leaved mixed forest. DBH change among 1-15 years is enlarged in the new small chart.
图3 三种恢复森林类型林分平均地上生物量与蓄积量的动态对比。 PSF, 人工云杉林; SBF, 次生桦木林; SMF, 次生针阔混交林。
Fig. 3 Dynamic comparisons of stand average aboveground biomass and volume among three recovery forest types. PSF, planted spruce (Picea asperata) forest; SBF, secondary birch (Betula spp.) forest; SMF, secondary coniferous and broad-leaved mixed forest.
图4 三种恢复途径林分地上净第一性生产力的动态变化。PSF, 人工云杉林; SBF, 次生桦木林; SMF, 次生针阔混交林。数据是3种恢复林型净第一性生产力的5年滑动平均值。 为表达清晰, 原数据未在图中显示。
Fig. 4 Dynamic changes of aboveground net primary productivity for stands with three restoration approaches. PSF, planted spruce (Picea asperata) forest; SBF, secondary birch (Betula spp.) forest; SMF, secondary coniferous and broad-leaved mixed forest. The data is five-year moving average of net primary productivity for three recovery forest types. Original data is not displayed in the chart for clarity.
图5 三种恢复森林类型林分密度与林龄的关系。PSF, 人工云杉林; SBF, 次生桦木林; SMF, 次生针阔混交林。
Fig. 5 Relationships between stand density and stand age of three recovery forest types. PSF, planted spruce (Picea asperata) forest; SBF, secondary birch (Betula spp.) forest; SMF, secondary coniferous and broad-leaved mixed forest. *, p < 0.05; **, p < 0.01.
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