生态环境学报 ›› 2026, Vol. 35 ›› Issue (5): 702-713.DOI: 10.16258/j.cnki.1674-5906.2026.05.004
张涛1,2(
), 杨慧3,*(
), 曹建华1,4, 周孟霞1,4, 康志强5,*(
)
收稿日期:2025-06-18
修回日期:2025-11-18
接受日期:2025-12-12
出版日期:2026-05-18
发布日期:2026-05-08
通讯作者:
*E-mail: 作者简介:张涛(1998年生),男,硕士研究生,主要从事岩溶区水文生态耦合过程研究。E-mail: sdlwzt1206@163.com
基金资助:
ZHANG Tao1,2(
), YANG Hui3,*(
), CAO Jianhua1,4, ZHOU Mengxia1,4, KANG Zhiqiang5,*(
)
Received:2025-06-18
Revised:2025-11-18
Accepted:2025-12-12
Online:2026-05-18
Published:2026-05-08
摘要:
植被净生态系统生产力(NEP)是衡量陆地生态系统碳源/汇功能的核心指标,其时空演变特征研究对区域碳中和意义重大。岩性作为地表物质组成基础单元,深刻影响NEP,但当前NEP研究多聚焦气候与植被耦合,对岩性分异的时空演变特征关注不足。基于1981-2020年中国NEP栅格数据及岩性分区资料,结合Theil-Sen趋势分析与Mann-Kendall检验,系统揭示广西NEP的时空演变规律及其与岩性的关联机制。结果显示:1)时间维度上,广西年NEP均值呈先降后升阶段性特征,1981-1991年波动下降,1991-2020年波动上升(2000年后增速显著),40年间均值范围211.35-279.56 g·m−2·a−1(以C计);2)空间格局上,碳源区集中于中部及南部部分地区,碳汇区分布于北部及西部(东南部碳汇强度高于西北部);2000-2020年,60.08%区域NEP显著增加(西北部为核心增长区),东部、东北部及西南部分地区NEP下降,碳汇功能退化;3)岩性差异显著影响NEP分异,岩溶区NEP均值(154.04-226.23 g·m−2·a−1)低于非岩溶区(253.40-313.33 g·m−2·a−1),但NEP增长速率更快;石灰岩区因石漠化治理与树种优化,2011年后反超白云岩区。研究揭示了岩性对NEP时空格局的关键调控作用,明确了不同岩性背景下生态恢复措施对碳汇提升的成效,可为岩溶地区制定差异化生态管理策略、增强区域碳汇功能提供科学支撑。
中图分类号:
张涛, 杨慧, 曹建华, 周孟霞, 康志强. 基于岩性分区的广西植被净生态系统生产力时空演变特征研究[J]. 生态环境学报, 2026, 35(5): 702-713.
ZHANG Tao, YANG Hui, CAO Jianhua, ZHOU Mengxia, KANG Zhiqiang. Study on the Spatiotemporal Evolution Characteristics of Vegetation Net Ecosystem Productivity in Guangxi Based on Lithological Zoning[J]. Ecology and Environmental Sciences, 2026, 35(5): 702-713.
| β | Z值 | 趋势类别 | 趋势特征 |
|---|---|---|---|
| β>0 | 2.58<Z | 4 | 极显著增加 |
| 1.96<Z≤2.58 | 3 | 显著增加 | |
| 1.65<Z≤1.96 | 2 | 微显著增加 | |
| Z≤1.65 | 1 | 不显著增加 | |
| β=0 | Z | 0 | 无变化 |
| β<0 | Z≤1.65 | −1 | 不显著减少 |
| 1.65<Z≤1.96 | −2 | 微显著减少 | |
| 1.96<Z≤2.58 | −3 | 显著减少 | |
| 2.58<Z | −4 | 极显著减少 |
表1 Mann-Kendall检验趋势类别
Table 1 Trend categories classified by Mann-Kendall test
| β | Z值 | 趋势类别 | 趋势特征 |
|---|---|---|---|
| β>0 | 2.58<Z | 4 | 极显著增加 |
| 1.96<Z≤2.58 | 3 | 显著增加 | |
| 1.65<Z≤1.96 | 2 | 微显著增加 | |
| Z≤1.65 | 1 | 不显著增加 | |
| β=0 | Z | 0 | 无变化 |
| β<0 | Z≤1.65 | −1 | 不显著减少 |
| 1.65<Z≤1.96 | −2 | 微显著减少 | |
| 1.96<Z≤2.58 | −3 | 显著减少 | |
| 2.58<Z | −4 | 极显著减少 |
| β | Z值 | 趋势特征 | 占比/% | 变化趋势 |
|---|---|---|---|---|
| β>0 | 2.58<Z | 极显著增加 | 36.18% | 增加(60.08%) |
| 1.96<Z≤2.58 | 显著增加 | 7.91% | ||
| 1.65<Z≤1.96 | 微显著增加 | 3.12% | ||
| Z≤1.65 | 不显著增加 | 12.88% | ||
| β=0 | Z | 无变化 | 22.97% | 不变(22.97%) |
| β<0 | Z≤1.65 | 不显著减少 | 8.69% | 减小(16.95%) |
| 1.65<Z≤1.96 | 微显著减少 | 1.27% | ||
| 1.96<Z≤2.58 | 显著减少 | 2.47% | ||
| 2.58<Z | 极显著减少 | 4.53% |
表2 2000年-2020年广西NEP变化趋势显著性比例
Table 2 Proportional distribution of significant NEP trends in Guangxi from 2000 to 2020
| β | Z值 | 趋势特征 | 占比/% | 变化趋势 |
|---|---|---|---|---|
| β>0 | 2.58<Z | 极显著增加 | 36.18% | 增加(60.08%) |
| 1.96<Z≤2.58 | 显著增加 | 7.91% | ||
| 1.65<Z≤1.96 | 微显著增加 | 3.12% | ||
| Z≤1.65 | 不显著增加 | 12.88% | ||
| β=0 | Z | 无变化 | 22.97% | 不变(22.97%) |
| β<0 | Z≤1.65 | 不显著减少 | 8.69% | 减小(16.95%) |
| 1.65<Z≤1.96 | 微显著减少 | 1.27% | ||
| 1.96<Z≤2.58 | 显著减少 | 2.47% | ||
| 2.58<Z | 极显著减少 | 4.53% |
图5 2000-2020年广西岩溶区与非岩溶区NEP变化趋势及其显著性
Figure 5 The changing trend and significance of NEP in the karst area and the non-karst area of Guangxi from 2000 to 2020
图6 2000-2020年广西石灰岩区、白云岩区及白云岩石灰岩共存区的NEP变化趋势及其显著性
Figure 6 The changing trends and significance of NEP in the limestone area, dolomite area, and the coexistence area of limestone and dolomite in Guangxi from 2000 to 2020
图9 1981-2020年广西、岩溶区、非岩溶区、石灰岩区、白云岩区及白云岩石灰岩共存区年均碳源碳汇占比变化
Figure 9 The changes in the average annual carbon source and carbon sink proportions in Guangxi, karst area, non-karst area, limestone area, dolomite area, and dolomite-limestone coexisting area from 1981 to 2020
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