生态环境学报 ›› 2026, Vol. 35 ›› Issue (3): 437-446.DOI: 10.16258/j.cnki.1674-5906.2026.03.010
赵师夷1(
), 李珺2, 赵旭1, 黄明昊1, 缑正洋1, 祝海彪1, 黄宏1,*(
)
收稿日期:2025-07-21
修回日期:2026-01-13
接受日期:2026-01-24
出版日期:2026-03-18
发布日期:2026-03-13
通讯作者:
*E-mail: 作者简介:赵师夷(2000年生),女,硕士研究生,主要研究方向为土壤有机碳。E-mail: 1144948924@qq.com
基金资助:
ZHAO Shiyi1(
), LI Jun2, ZHAO Xu1, HUANG Minghao1, GOU Zhengyang1, ZHU Haibiao1, HUANG Hong1,*(
)
Received:2025-07-21
Revised:2026-01-13
Accepted:2026-01-24
Online:2026-03-18
Published:2026-03-13
摘要:
滨海湿地生态系统具有较高的碳储存能力,而湿地土壤有机碳组分特征对于认识滨海湿地碳循环过程至关重要。该研究对崇明东滩不同植被类型覆盖的湿地开展调查与样品采集,分析了土壤有机碳组分及理化性质;通过相关性和差异性显著分析,探讨土壤有机碳组分在潮滩梯度与不同植被类型覆盖下的分布特征,以及土壤理化性质对其分布的影响。结果表明:崇明东滩湿地土壤总有机碳(TOC)质量分数均值为(9.64±4.23)g∙kg−1,其中互花米草(Spartina alterniflora)湿地土壤TOC质量分数最高,为(13.9±4.28)g∙kg−1,TOC与惰性有机碳(ROC)相关性最强;活性有机碳组分(LOC)含量在互花米草的聚集性明显;ROC含量表现为高潮滩区域[(5.81±1.41)g∙kg−1]>中潮滩[(3.68±1.52)g∙kg−1]>低潮滩[(2.35±1.01)g∙kg−1]的潮滩梯度特征;崇明东滩湿地土壤有机碳组分及理化因子在南、北部呈现出不同的空间聚集性,在北部高潮滩区TOC、LOC含量较高,土壤盐度北部较高,而粒径则南部较高;湿地土壤有机碳及其组分与理化因子相关性分析显示,TOC含量与土壤含水率及中值粒径呈现显著负相关(p<0.05),而与盐度呈现显著正相关(p<0.05),崇明东滩湿地土壤的中值粒径和盐度是有机碳含量的主控因子。
中图分类号:
赵师夷, 李珺, 赵旭, 黄明昊, 缑正洋, 祝海彪, 黄宏. 崇明东滩湿地土壤有机碳组分空间异质性及影响因素[J]. 生态环境学报, 2026, 35(3): 437-446.
ZHAO Shiyi, LI Jun, ZHAO Xu, HUANG Minghao, GOU Zhengyang, ZHU Haibiao, HUANG Hong. Spatial Heterogeneity and Influencing Factors of Soil Organic Carbon Fractions in Chongming Dongtan Wetland[J]. Ecology and Environmental Sciences, 2026, 35(3): 437-446.
| 湿地类型 | 点位 | 土壤盐度/ (g∙kg−1) | pH | 水分质量分数/% | 中值粒径/ µm |
|---|---|---|---|---|---|
| 光滩 | CN11-13 | 8.72±1.52 | 7.90±0.1 | 53.33±2.95 | 30.44±2.25 |
| CS11-13 | 4.21±1.83 | 7.92±0.07 | 62.12±3.15 | 33.42±1.86 | |
| 互花米草 覆盖区 | CN21-23 | 4.77±0.49 | 8.37±0.15 | 42.11±1.12 | 11.09±3.45 |
| CN31-33 | 5.35±0.17 | 7.85±0.25 | 43.26±1.34 | 11.75±2.22 | |
| 海三棱蔍草覆盖区 | CS21-23 | 2.34±1.22 | 7.92±0.06 | 46.35±1.82 | 19.92±1.32 |
| 芦苇覆盖区 | CS31-33 | 3.34±0.39 | 8.15±0.1 | 38.72±2.61 | 16.65±2.45 |
表1 崇明东滩不同湿地类型土壤基本理化性质
Table 1 Basic physical and chemical properties of soils of different vegetation types in Chongming Dongtan, China
| 湿地类型 | 点位 | 土壤盐度/ (g∙kg−1) | pH | 水分质量分数/% | 中值粒径/ µm |
|---|---|---|---|---|---|
| 光滩 | CN11-13 | 8.72±1.52 | 7.90±0.1 | 53.33±2.95 | 30.44±2.25 |
| CS11-13 | 4.21±1.83 | 7.92±0.07 | 62.12±3.15 | 33.42±1.86 | |
| 互花米草 覆盖区 | CN21-23 | 4.77±0.49 | 8.37±0.15 | 42.11±1.12 | 11.09±3.45 |
| CN31-33 | 5.35±0.17 | 7.85±0.25 | 43.26±1.34 | 11.75±2.22 | |
| 海三棱蔍草覆盖区 | CS21-23 | 2.34±1.22 | 7.92±0.06 | 46.35±1.82 | 19.92±1.32 |
| 芦苇覆盖区 | CS31-33 | 3.34±0.39 | 8.15±0.1 | 38.72±2.61 | 16.65±2.45 |
图3 崇明东滩湿地土壤理化参数与有机碳组分间的相关性特征
Figure 3 Correlation characteristics between soil physicochemical parameters and organic carbon components in Chongming Dongtan Wetland *:p<0.05;**:p<0.01
| 理化参数 | 莫兰指数 | Z值 | p值 |
|---|---|---|---|
| S | 0.52 | 3.98 | <0.001 |
| pH | 0.16 | 1.58 | 0.11 |
| w | 0.14 | 1.02 | 0.35 |
| D50 | 0.25 | 2.85 | <0.05 |
| LOC | 0.32 | 2.51 | <0.05 |
| ROC | 0.22 | 1.78 | 0.08 |
| TOC | 0.35 | 2.71 | <0.05 |
表2 湿地土壤理化参数全局空间自相关分析结果
Table 2 Global spatial autocorrelation analysis results of physical and chemical parameters in wetland soils
| 理化参数 | 莫兰指数 | Z值 | p值 |
|---|---|---|---|
| S | 0.52 | 3.98 | <0.001 |
| pH | 0.16 | 1.58 | 0.11 |
| w | 0.14 | 1.02 | 0.35 |
| D50 | 0.25 | 2.85 | <0.05 |
| LOC | 0.32 | 2.51 | <0.05 |
| ROC | 0.22 | 1.78 | 0.08 |
| TOC | 0.35 | 2.71 | <0.05 |
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