Chin J Plant Ecol ›› 2025, Vol. 49 ›› Issue (4): 526-539.DOI: 10.17521/cjpe.2024.0253 cstr: 32100.14.cjpe.2024.0253
• Research Articles • Previous Articles Next Articles
LI Lin1, HUANG Jia-Fang1,3,*(), DING Zhong-Hao1, GUO Ping-Ping3, CAI Yuan-Bin2, LI Shi-Hua4, LI Yun-Qin2, LUO Min2,*(
)
Received:
2024-07-31
Accepted:
2025-01-03
Online:
2025-04-20
Published:
2025-04-18
Contact:
HUANG Jia-Fang, LUO Min
Supported by:
LI Lin, HUANG Jia-Fang, DING Zhong-Hao, GUO Ping-Ping, CAI Yuan-Bin, LI Shi-Hua, LI Yun-Qin, LUO Min. Impact of increased inundation height on the net ecosystem CO2 exchange in a Cyperus malaccensis tidal marsh[J]. Chin J Plant Ecol, 2025, 49(4): 526-539.
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URL: https://www.plant-ecology.com/EN/10.17521/cjpe.2024.0253
Fig. 1 Location of study site for carbon flux research and a schematic diagram of marsh organ experimental platform in the Shanyutan tidal marsh of the Minjiang River Estuary. A, Diagram of the Minjiang River Estuary. B, Diagram of the study area (the red rectangle) in the Shanyutan tidal marsh of the Minjiang River Estuary. C, Schematic diagram of the “marsh organ” experiment. CK, control.
Fig. 2 Monthly dynamics of daily mean air temperature, daily mean and maximum photosynthetically active radiation (PAR) in the Cyperus malaccensis tidal marsh of the Minjiang River Estuary.
植物性状特征 Plant trait characteristic | 淹水处理 Inundation treatment | ||||
---|---|---|---|---|---|
CK | CK + 20 cm | CK + 40 cm | F | p | |
AGB (kg·m-2) | 5.0 ± 0.2a | 4.4 ± 0.6ab | 3.5 ± 0.6b | 5.495 | <0.05 |
BGB (kg·m-2) | 3.3 ± 0.5b | 4.4 ± 0.1ab | 5.1 ± 0.3a | 10.406 | <0.05 |
Pn (μmol·m-2·s-1)1) | 33.1 ± 2.3a | 28.9 ± 1.9ab | 26.0 ± 3.5b | 9.956 | <0.05 |
gs (mmol·m-2·s-1)1) | 241.3 ± 11.5a | 198.0 ± 10.8b | 167.7 ± 11.7c | 31.989 | <0.001 |
Ci (μmol·mol-1)1) | 309.0 ± 20.1a | 274.0 ± 9.5ab | 277.9 ± 28.7b | 11.627 | <0.01 |
Table 1 Plant traits under three inundation treatments in the Cyperus malaccensis tidal marsh of the Minjiang River Estuary (mean ± SD)
植物性状特征 Plant trait characteristic | 淹水处理 Inundation treatment | ||||
---|---|---|---|---|---|
CK | CK + 20 cm | CK + 40 cm | F | p | |
AGB (kg·m-2) | 5.0 ± 0.2a | 4.4 ± 0.6ab | 3.5 ± 0.6b | 5.495 | <0.05 |
BGB (kg·m-2) | 3.3 ± 0.5b | 4.4 ± 0.1ab | 5.1 ± 0.3a | 10.406 | <0.05 |
Pn (μmol·m-2·s-1)1) | 33.1 ± 2.3a | 28.9 ± 1.9ab | 26.0 ± 3.5b | 9.956 | <0.05 |
gs (mmol·m-2·s-1)1) | 241.3 ± 11.5a | 198.0 ± 10.8b | 167.7 ± 11.7c | 31.989 | <0.001 |
Ci (μmol·mol-1)1) | 309.0 ± 20.1a | 274.0 ± 9.5ab | 277.9 ± 28.7b | 11.627 | <0.01 |
土壤理化指标 Soil physicochemical index | 淹水处理 Inundation treatment | ||||
---|---|---|---|---|---|
CK | CK + 20 cm | CK + 40 cm | F | p | |
pH | 6.7 ± 0.2a | 6.8 ± 0.3a | 6.7 ± 1.2a | 2.398 | 0.172 |
SOC (mg·g-1) | 13.7 ± 1.3a | 11.1 ± 2.1ab | 9.4 ± 1.2b | 5.518 | <0.05 |
C:N | 11.6 ± 2.1b | 11.5 ± 0.5b | 14.9 ± 0.7a | 6.748 | <0.05 |
SO42- (mmol·L-1) | 5.2 ± 0.6a | 4.5 ± 1.0a | 4.7 ± 1.0a | 3.425 | 0.102 |
Cl- (mmol·L-1) | 82.5 ± 25.5a | 85.6 ± 6.5a | 83.0 ± 17.5a | 1.436 | 0.309 |
Table 2 Soil physicochemical indexes under three inundation treatments in the Cyperus malaccensis tidal marsh of the Minjiang River Estuary (mean ± SD)
土壤理化指标 Soil physicochemical index | 淹水处理 Inundation treatment | ||||
---|---|---|---|---|---|
CK | CK + 20 cm | CK + 40 cm | F | p | |
pH | 6.7 ± 0.2a | 6.8 ± 0.3a | 6.7 ± 1.2a | 2.398 | 0.172 |
SOC (mg·g-1) | 13.7 ± 1.3a | 11.1 ± 2.1ab | 9.4 ± 1.2b | 5.518 | <0.05 |
C:N | 11.6 ± 2.1b | 11.5 ± 0.5b | 14.9 ± 0.7a | 6.748 | <0.05 |
SO42- (mmol·L-1) | 5.2 ± 0.6a | 4.5 ± 1.0a | 4.7 ± 1.0a | 3.425 | 0.102 |
Cl- (mmol·L-1) | 82.5 ± 25.5a | 85.6 ± 6.5a | 83.0 ± 17.5a | 1.436 | 0.309 |
Fig. 3 Monthly dynamics of soil dissolved organic carbon (DOC) concentrations and oxidation-reduction potential (ORP) in the Cyperus malaccensis tidal marsh of the Minjiang River Estuary under three inundation treatments (mean ± SD). p < 0.05 was significant difference, p < 0.01 was highly significant difference, and p < 0.001 was extremely significant difference. CK, control.
Fig. 4 Monthly dynamics of ecosystem respiration (ER), gross primary productivity (GPP) and net ecosystem CO2 exchange (NEE) in the Cyperus malaccensis tidal marsh of the Minjiang River Estuary under three inundation treatments (mean ± SD). p < 0.05 was significant difference, p < 0.01 was highly significant difference, and p < 0.001 was extremely significant difference. CK, control.
Fig. 5 Relationship between ecosystem respiration (ER) and soil physiochemical properties in the Cyperus malaccensis tidal marsh of the Minjiang River Estuary under three inundation treatments. DOC, dissolved organic carbon; ORP, oxidation-reduction potential. p < 0.05 was significant correlated, p < 0.01 was highly significant correlated, and p < 0.001 was extremely significant correlated. CK, control.
Fig. 6 Mean monthly ecosystem respiration (ER), gross primary productivity (GPP) and net ecosystem CO2 exchange (NEE) in the Cyperus malaccensis tidal marsh of the Minjiang River Estuary under three inundation treatments (mean ± SD). Different uppercase letters represent significant differences under different inundation treatments (p < 0.05 was significant, p < 0.01 was highly significant, and p < 0.001 was extremely significant). CK, control.
Fig. 7 Differences in net ecosystem CO2 exchange fluxes (NEE), ecosystem respiration (ER) and gross primary productivity (GPP) various wetlands globally.
Fig. 8 Response of the carbon budget process of the Cyperus malaccensis tidal marsh of the Minjiang River Estuary ecosystem to enhanced inundation. AGB, aboveground biomass; BGB, belowground biomass; Ci, intercellular CO2 concentration; DOC, dissolved organic carbon concentration; ER, ecosystem respiration; GPP, gross primary productivity; gs, stomatal conductance; NEE, net ecosystem CO2 exchange; ORP, oxidation-reduction potential; Pn, net photosynthetic rate.
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