生态环境学报 ›› 2026, Vol. 35 ›› Issue (6): 856-864.DOI: 10.16258/j.cnki.1674-5906.2026.06.003
王丹妮1,2,4(
), 曾荣菊3, 林诗英3, 吴彦3, 李雅颖1,2, 俞永祥1,2,3,*(
), 姚槐应1,2,3
收稿日期:2025-11-09
修回日期:2026-04-03
接受日期:2026-04-28
出版日期:2026-06-18
发布日期:2026-06-08
通讯作者:
* 俞永祥,E-mail: 作者简介:王丹妮(1999年生),女,硕士研究生,主要研究方向为土壤活性碳循环。E-mail: wangdanni25@mails.ucas.ac.cn
基金资助:
WANG Danni1,2,4(
), ZENG Rongju3, LIN Shiying3, WU Yan3, LI Yaying1,2, YU Yongxiang1,2,3,*(
), YAO Huaiying1,2,3
Received:2025-11-09
Revised:2026-04-03
Accepted:2026-04-28
Online:2026-06-18
Published:2026-06-08
摘要:
陆地生态系统土壤固碳潜力突出,合理调控土壤碳储量是减缓气候变暖、实现“碳中和”的重要途径。针对宁波市陆地土壤碳库空间异质性大、固碳潜力不明的问题,以该地区森林、农田和城市绿地土壤为研究对象,采用野外调查、室内分析、数值计算等方法评估了1 m深度内不同陆地生态系统土壤有机碳(SOC)储量分布及固碳潜力。结果显示,不同生态系统SOC差异显著,表现为农田>森林>城市绿地;土壤剖面SOC垂直分布特征显著,而且存在较大的空间异质性。1 m深度土壤总碳储量表现为森林(35.8 Tg)>农田(29.0 Tg)>城市绿地(16.6 Tg)。固碳潜力上看,森林土壤固碳潜力最高(4804.5 Gg),其中30-60 cm土层固碳潜力大;农田土壤固碳潜力次之(2462.1 Gg),但不同深度的土壤固碳潜力差异不大;城市绿地土壤固碳潜力最低(1363.5 Gg),其中60-100 cm深度土层固碳潜力突出。从土壤类型上看,森林暗色土、农田人为土和聚铁网纹土以及城市绿地工程土均在60-100 cm土层表现出较高的固碳潜力。宁波市陆地生态系统土壤固碳潜力较大,有效提升该地区土壤碳储量对实现“碳中和”目标具有重要意义。
中图分类号:
王丹妮, 曾荣菊, 林诗英, 吴彦, 李雅颖, 俞永祥, 姚槐应. 宁波市陆地生态系统土壤碳储量及固碳潜力评估[J]. 生态环境学报, 2026, 35(6): 856-864.
WANG Danni, ZENG Rongju, LIN Shiying, WU Yan, LI Yaying, YU Yongxiang, YAO Huaiying. Evaluation of Soil Carbon Storage and Carbon Sequestration Potential in Ningbo’s Terrestrial Ecosystems[J]. Ecology and Environmental Sciences, 2026, 35(6): 856-864.
图1 宁波市森林、农田和城市绿地土壤采样点分布图 该图基于审图号为GS(2024)0650号的标准地图制作,底图边界无修改。下同
Figure 1 Distribution map of forest, cropland and city green spaces soil sampling sites in Ningbo
图2 宁波市森林、农田和城市绿地土壤1 m深度有机碳储量分布图
Figure 2 Spatial distribution map of soil organic carbon storage at 0?1 m depth in forests, croplands and urban green spaces of Ningbo
| 生态系统 | 土壤类型 | 土壤固碳潜力/Gg | 单位面积土壤固碳潜力/(Mg·hm−2) | ||||||
|---|---|---|---|---|---|---|---|---|---|
| 0-30 cm | 30-60 cm | 60-100 cm | 0-100 cm | 0-30 cm | 30-60 cm | 60-100 cm | |||
| 森林 | 低活性强酸土 | 91.6 | 34.9 | 40.7 | 167.0 | 3.7 | 1.4 | 1.7 | |
| 人为土 | 130.8 | 217.7 | 98.4 | 446.9 | 3.0 | 4.9 | 2.2 | ||
| 疏松岩性土 | 345.2 | 543.8 | 218.5 | 1107.5 | 3.7 | 5.8 | 2.3 | ||
| 暗色土 | 709.1 | 563.0 | 1811.1 | 3083.3 | 3.3 | 2.6 | 8.3 | ||
| 农田 | 人为土 | 555.6 | 528.1 | 609.6 | 1693.3 | 5.9 | 5.6 | 6.4 | |
| 冲积土 | 17.6 | 3.2 | 3.2 | 24.0 | 0.3 | 0.1 | 0.1 | ||
| 聚铁网纹土 | 151.9 | 204.0 | 253.1 | 608.9 | 3.1 | 4.1 | 5.1 | ||
| 工程土 | 5.7 | 5.7 | 2.6 | 14.0 | 0.5 | 0.5 | 0.2 | ||
| 暗色土 | 12.2 | 41.0 | 68.6 | 121.8 | 0.3 | 1.0 | 1.7 | ||
| 城市绿地 | 工程土 | 335.1 | 318.9 | 599.9 | 1254.1 | 4.2 | 4.0 | 7.4 | |
| 聚铁网纹土 | 6.5 | 30.1 | 16.8 | 53.4 | 0.5 | 2.3 | 1.3 | ||
| 人为土 | 11.9 | 18.3 | 25.8 | 56.0 | 0.4 | 0.7 | 0.9 | ||
表1 宁波市不同生态系统土壤固碳潜力及单位面积固碳潜力
Table 1 Soil carbon sequestration potential and its per-unit area value across different ecosystems in Ningbo
| 生态系统 | 土壤类型 | 土壤固碳潜力/Gg | 单位面积土壤固碳潜力/(Mg·hm−2) | ||||||
|---|---|---|---|---|---|---|---|---|---|
| 0-30 cm | 30-60 cm | 60-100 cm | 0-100 cm | 0-30 cm | 30-60 cm | 60-100 cm | |||
| 森林 | 低活性强酸土 | 91.6 | 34.9 | 40.7 | 167.0 | 3.7 | 1.4 | 1.7 | |
| 人为土 | 130.8 | 217.7 | 98.4 | 446.9 | 3.0 | 4.9 | 2.2 | ||
| 疏松岩性土 | 345.2 | 543.8 | 218.5 | 1107.5 | 3.7 | 5.8 | 2.3 | ||
| 暗色土 | 709.1 | 563.0 | 1811.1 | 3083.3 | 3.3 | 2.6 | 8.3 | ||
| 农田 | 人为土 | 555.6 | 528.1 | 609.6 | 1693.3 | 5.9 | 5.6 | 6.4 | |
| 冲积土 | 17.6 | 3.2 | 3.2 | 24.0 | 0.3 | 0.1 | 0.1 | ||
| 聚铁网纹土 | 151.9 | 204.0 | 253.1 | 608.9 | 3.1 | 4.1 | 5.1 | ||
| 工程土 | 5.7 | 5.7 | 2.6 | 14.0 | 0.5 | 0.5 | 0.2 | ||
| 暗色土 | 12.2 | 41.0 | 68.6 | 121.8 | 0.3 | 1.0 | 1.7 | ||
| 城市绿地 | 工程土 | 335.1 | 318.9 | 599.9 | 1254.1 | 4.2 | 4.0 | 7.4 | |
| 聚铁网纹土 | 6.5 | 30.1 | 16.8 | 53.4 | 0.5 | 2.3 | 1.3 | ||
| 人为土 | 11.9 | 18.3 | 25.8 | 56.0 | 0.4 | 0.7 | 0.9 | ||
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