植物生态学报 ›› 2016, Vol. 40 ›› Issue (10): 1037-1048.DOI: 10.17521/cjpe.2016.0020 cstr: 32100.14.cjpe.2016.0020
所属专题: 碳循环
孙鹏森1,,A;*, 刘宁2, 刘世荣1, 孙阁3
出版日期:2016-10-10
发布日期:2016-11-02
Peng-Sen SUN1,*, Ning LIU2, Shi-Rong LIU1, Ge SUN3
Online:2016-10-10
Published:2016-11-02
摘要:
森林生态系统的产水量与固碳效益之间存在着一种可交易的平衡关系。基于WaSSI-C水碳耦合模型和趋势分析, 研究了1982-2006年川西杂古脑河上游22个子流域内不同植被类型空间分布对水碳平衡的影响并分析了其水碳耦合关系, 发现: 1)针叶林主导的流域在生长季增加土壤水分入渗的功能明显高于其他植被类型, 但不足以补偿其高蒸散带来的水分消耗, 因而其年平均土壤含水量明显低于高山草甸和混交林类型; 且森林土壤含水量随着森林覆盖率的升高而降低。2) 25年的土壤水分蓄变量的平均值, 高山草甸流域为-44 mm, 混交林为-18 mm, 针叶林为-5 mm, 说明川西亚高山植被的整体维持稳定产水量及其潜力在下降, 其中高山草甸流域下降趋势尤为显著。3)流域产流量和净生态系统生产力具有显著负相关性, 且不同植被组成对固碳和产水效益的转化具有重要影响: 高山草甸主导的子流域具有较高的产水量和较低的固碳能力, 常绿针叶林主导的子流域具有较高固碳能力和较低产水量, 且森林覆盖率越高, 产水量越低。三种植被类型的净生态系统生产力在研究期间均呈现上升趋势, 且高山草甸的上升趋势显著。
孙鹏森, 刘宁, 刘世荣, 孙阁. 川西亚高山流域水碳平衡研究. 植物生态学报, 2016, 40(10): 1037-1048. DOI: 10.17521/cjpe.2016.0020
Peng-Sen SUN, Ning LIU, Shi-Rong LIU, Ge SUN. Trade-offs between water yield and carbon sequestration for sub-alpine catchments in western Sichuan, China. Chinese Journal of Plant Ecology, 2016, 40(10): 1037-1048. DOI: 10.17521/cjpe.2016.0020
图2 杂古脑河上游各子流域的土地覆盖类型分布图(图中数字表示子流域编号)。
Fig. 2 Land cover types for sub-catchments in upper reaches of Zagunao river (numbers in graph are serial numbers of sub-catchments).
| 子流域编号 Serial number of sub-catchment | 地形特征 Topography characteristics | 植被组成 Vegetation composition | ||||||
|---|---|---|---|---|---|---|---|---|
| 面积 Area (km2) | 坡度 Slope (°) | 平均海拔 Mean altitude (m) | 针叶林覆盖率 Coniferous forest coverage (%) | 森林覆盖率 Forest coverage (%) | 高山草甸覆盖率 Alpine meadow coverage (%) | 主导植被类型 Dominant vegetation type | ||
| 3 | 20.0 | 51.5 | 4 077 | 91 | 99 | 0 | 针叶林 Coniferous forest | |
| 5 | 89.2 | 56.4 | 3 838 | 54 | 65 | 33 | ||
| 8 | 49.8 | 59.4 | 3 924 | 61 | 81 | 19 | ||
| 10 | 84.4 | 63.2 | 3 948 | 50 | 75 | 25 | ||
| 15 | 47.6 | 76.5 | 3 355 | 50 | 64 | 36 | ||
| 17 | 25.6 | 68.8 | 3 647 | 60 | 68 | 32 | ||
| 11 | 195.9 | 58.4 | 4 010 | 28 | 53 | 42 | 混交林 Mixed forest | |
| 12 | 127.9 | 69.3 | 3 322 | 28 | 6 | 38 | ||
| 18 | 171.2 | 65.9 | 3 937 | 18 | 5 | 44 | ||
| 19 | 59.6 | 71.6 | 3 866 | 24 | 76 | 23 | ||
| 21 | 112.5 | 66.7 | 4 017 | 39 | 58 | 34 | ||
| 22 | 66.0 | 59.1 | 3 543 | 22 | 48 | 43 | ||
| 1 | 251.5 | 49.4 | 4 004 | 27 | 48 | 51 | 高山草甸 Alpine meadow | |
| 2 | 146.2 | 54.9 | 3 995 | 25 | 47 | 50 | ||
| 4 | 221.7 | 58.9 | 3 371 | 21 | 41 | 55 | ||
| 6 | 82.5 | 59.3 | 3 672 | 33 | 52 | 49 | ||
| 7 | 132.7 | 61.3 | 3 446 | 30 | 47 | 51 | ||
| 9 | 149.1 | 60.9 | 3 628 | 37 | 43 | 57 | ||
| 13 | 139.8 | 73.6 | 3 348 | 32 | 43 | 55 | ||
| 14 | 87.9 | 69.6 | 3 998 | 33 | 45 | 51 | ||
| 16 | 81.2 | 70.6 | 3 348 | 36 | 51 | 50 | ||
| 20 | 96.9 | 66.6 | 4 016 | 29 | 43 | 54 | ||
表1 杂谷脑河流域上游各子流域的地形及植被组成
Table 1 Topography and vegetation composition for sub-catchments in upper reaches of Zagunao river
| 子流域编号 Serial number of sub-catchment | 地形特征 Topography characteristics | 植被组成 Vegetation composition | ||||||
|---|---|---|---|---|---|---|---|---|
| 面积 Area (km2) | 坡度 Slope (°) | 平均海拔 Mean altitude (m) | 针叶林覆盖率 Coniferous forest coverage (%) | 森林覆盖率 Forest coverage (%) | 高山草甸覆盖率 Alpine meadow coverage (%) | 主导植被类型 Dominant vegetation type | ||
| 3 | 20.0 | 51.5 | 4 077 | 91 | 99 | 0 | 针叶林 Coniferous forest | |
| 5 | 89.2 | 56.4 | 3 838 | 54 | 65 | 33 | ||
| 8 | 49.8 | 59.4 | 3 924 | 61 | 81 | 19 | ||
| 10 | 84.4 | 63.2 | 3 948 | 50 | 75 | 25 | ||
| 15 | 47.6 | 76.5 | 3 355 | 50 | 64 | 36 | ||
| 17 | 25.6 | 68.8 | 3 647 | 60 | 68 | 32 | ||
| 11 | 195.9 | 58.4 | 4 010 | 28 | 53 | 42 | 混交林 Mixed forest | |
| 12 | 127.9 | 69.3 | 3 322 | 28 | 6 | 38 | ||
| 18 | 171.2 | 65.9 | 3 937 | 18 | 5 | 44 | ||
| 19 | 59.6 | 71.6 | 3 866 | 24 | 76 | 23 | ||
| 21 | 112.5 | 66.7 | 4 017 | 39 | 58 | 34 | ||
| 22 | 66.0 | 59.1 | 3 543 | 22 | 48 | 43 | ||
| 1 | 251.5 | 49.4 | 4 004 | 27 | 48 | 51 | 高山草甸 Alpine meadow | |
| 2 | 146.2 | 54.9 | 3 995 | 25 | 47 | 50 | ||
| 4 | 221.7 | 58.9 | 3 371 | 21 | 41 | 55 | ||
| 6 | 82.5 | 59.3 | 3 672 | 33 | 52 | 49 | ||
| 7 | 132.7 | 61.3 | 3 446 | 30 | 47 | 51 | ||
| 9 | 149.1 | 60.9 | 3 628 | 37 | 43 | 57 | ||
| 13 | 139.8 | 73.6 | 3 348 | 32 | 43 | 55 | ||
| 14 | 87.9 | 69.6 | 3 998 | 33 | 45 | 51 | ||
| 16 | 81.2 | 70.6 | 3 348 | 36 | 51 | 50 | ||
| 20 | 96.9 | 66.6 | 4 016 | 29 | 43 | 54 | ||
图3 杂古脑河上游各子流域的年降水量(A)、年蒸散量(B)和年径流量(C)的空间分布(图中数字表示子流域编号)。
Fig. 3 Spatial patterns of mean annual precipitation (A), evapotranspiration (B) and runoff (C) of Zagunao upper reaches (numbers in graph are serial numbers of sub-catchments).
图4 杂古脑流域平均年总生态系统生产力(A)、生态系统呼吸(B)和净生态系统交换(C)的空间分布(图中数字表示子流域 编号)。
Fig. 4 Spatial patterns of annual gross ecosystem productivity (A), net ecosystem exchange (B), respiration of ecosystem (C) of Zagunao upper reaches (numbers in graph are serial numbers of sub-catchments).
图6 土壤含水量(A)、土壤蓄水变量(B)与植被覆盖率之间的关系(图B中的数字为子流域编号, 圆圈内为水分流失严重的子流域)。
Fig. 6 The relationships between forest coverage and soil water content (A), and soil water storage change (B) (Numbers in Figure B denote sub-catchments and the severe water loss sub-catchments are inside circle).
图7 不同主导植被类型流域的生长季平均径流量与净生态系统生产力的变化趋势检验(Spearman’s Rho)。
Fig. 7 Spearman’s Rho trend analysis of runoff and net ecosystem productivity for different vegetation dominated catchments.
图8 杂谷脑河流域上游产水量与净生态系统生产力的关系(图中数值标志为子流域森林覆盖率)。
Fig. 8 Relationship between water yield and net ecosystem productivity in the upper reaches of Zagunao river (numerical values in plot denote forest coverage for sub-catchment).
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