Chin J Plant Ecol ›› 2023, Vol. 47 ›› Issue (9): 1310-1321.DOI: 10.17521/cjpe.2022.0176
Special Issue: 全球变化与生态系统; 土壤呼吸; 微生物生态学
• Research Articles • Previous Articles Next Articles
LI Bing1,2, ZHU Wan-Wan3, HAN Cui1, YU Hai-Long3, HUANG Ju-Ying2,*()
Received:
2022-05-05
Accepted:
2022-09-07
Online:
2023-09-20
Published:
2023-09-28
Contact:
* HUANG Ju-Ying(Supported by:
LI Bing, ZHU Wan-Wan, HAN Cui, YU Hai-Long, HUANG Ju-Ying. Soil respiration and its influencing factors in a desert steppe in northwestern China under changing precipitation regimes[J]. Chin J Plant Ecol, 2023, 47(9): 1310-1321.
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URL: https://www.plant-ecology.com/EN/10.17521/cjpe.2022.0176
差异来源 Difference source | df | 8:00-10:00 | 15:00-17:00 |
---|---|---|---|
降水量处理 Precipitation treatment (α) | 4 | 13.198** | 37.013** |
测定时间 Measuring time (β) | 4 | 24.532** | 37.278** |
降水量处理×测定时间 Interaction of α and β | 16 | 0.520 | 0.678 |
Table 1 Repeated measurement ANOVA of precipitation and measuring time on soil respiration rate in a desert steppe
差异来源 Difference source | df | 8:00-10:00 | 15:00-17:00 |
---|---|---|---|
降水量处理 Precipitation treatment (α) | 4 | 13.198** | 37.013** |
测定时间 Measuring time (β) | 4 | 24.532** | 37.278** |
降水量处理×测定时间 Interaction of α and β | 16 | 0.520 | 0.678 |
Fig. 2 Effects of precipitation change on soil respiration rate from June to October in a desert steppe (mean ± SE). W1, 50% reduction in precipitation; W2, 30% reduction in precipitation; W3, natural precipitation; W4, 30% increase in precipitation; W5, 50% increase in precipitation. Different lowercase letters indicate significant differences among the precipitation treatments under the same measuring time (p < 0.05).
差异来源 Differences source | df | ST | SWC | |
---|---|---|---|---|
8:00-10:00 | 15:00-17:00 | 8:00-10:00 | ||
降水量处理 Precipitation treatment (α) | 4 | 3.707* | 2.276 | 27.601** |
测定时间 Measuring time (β) | 4 | 57.317** | 146.775** | 15.003** |
降水量处理×测定时间 Interaction of α and β | 16 | 0.108 | 0.306 | 1.879 |
Table 2 Repeated measurement ANOVA of precipitation and measuring time on soil temperature (ST) and soil water content (SWC) in a desert steppe
差异来源 Differences source | df | ST | SWC | |
---|---|---|---|---|
8:00-10:00 | 15:00-17:00 | 8:00-10:00 | ||
降水量处理 Precipitation treatment (α) | 4 | 3.707* | 2.276 | 27.601** |
测定时间 Measuring time (β) | 4 | 57.317** | 146.775** | 15.003** |
降水量处理×测定时间 Interaction of α and β | 16 | 0.108 | 0.306 | 1.879 |
Fig. 3 Effects of precipitation change on soil temperature from June to October in a desert steppe (mean ± SE). W1, 50% reduction in precipitation; W2, 30% reduction in precipitation; W3, natural precipitation; W4, 30% increase in precipitation; W5, 50% increase in precipitation. Different lowercase letters indicate significant differences among the precipitation treatments under the same measuring time (p < 0.05).
Fig. 4 Effects of precipitation change on soil water content from June to October in a desert steppe (mean ± SE). W1, 50% reduction in precipitation; W2, 30% reduction in precipitation; W3, natural precipitation; W4, 30% increase in precipitation; W5, 50% increase in precipitation. Different lowercase letters indicate significant differences among the precipitation treatments under the same measuring time (p < 0.05).
指标 Index | 处理 Treatment | ||||
---|---|---|---|---|---|
W1 | W2 | W3 | W4 | W5 | |
pH | 8.52 ± 0.05bc | 8.58 ± 0.04ab | 8.43 ± 0.04c | 8.67 ± 0.05a | 8.66 ± 0.04a |
EC | 89.97 ± 0.88a | 93.37 ± 2.44a | 128.70 ± 18.49a | 289.67 ± 22.93a | 358.00 ± 38.19a |
SOC | 2.96 ± 0.08b | 3.25 ± 0.50ab | 3.34 ± 0.17ab | 3.38 ± 0.24ab | 3.70 ± 0.12a |
TN | 0.48 ± 0.00a | 0.49 ± 0.01a | 0.48 ± 0.01a | 0.43 ± 0.02b | 0.43 ± 0.01b |
TP | 0.34 ± 0.00a | 0.29 ± 0.00b | 0.27 ± 0.01c | 0.28 ± 0.00bc | 0.27 ± 0.00c |
NO3--N | 5.50 ± 0.41a | 5.08 ± 0.76ab | 3.28 ± 0.05b | 5.19 ± 0.91a | 5.81 ± 0.42a |
NH4+-N | 2.91 ± 0.23a | 3.59 ± 0.68a | 5.44 ± 1.12a | 5.71 ± 1.84a | 5.31 ± 3.34a |
AP | 1.56 ± 0.13a | 1.62 ± 0.51a | 1.72 ± 0.28a | 2.14 ± 0.30a | 2.47 ± 0.68a |
SA | 318.41 ± 33.75c | 359.39 ± 41.44bc | 381.78 ± 33.90abc | 434.93 ± 36.46ab | 474.67 ± 30.07a |
UA | 27.85 ± 3.86b | 30.68 ± 0.67b | 30.95 ± 1.96b | 45.34 ± 4.52a | 45.70 ± 4.82a |
PA | 44.58 ± 0.32bc | 40.89 ± 3.01c | 43.88 ± 2.97bc | 49.02 ± 2.42ab | 55.60 ± 1.35a |
MBC | 99.05 ± 9.57ab | 77.05 ± 20.59ab | 46.68 ± 14.32b | 100.24 ± 27.02ab | 108.73 ± 8.91a |
MBN | 48.97 ± 2.28a | 5.90 ± 0.80a | 7.45 ± 1.74a | 15.10 ± 7.95a | 19.91 ± 8.67a |
MBP | 1.76 ± 0.73b | 3.56 ± 0.40a | 1.76 ± 0.76b | 1.14 ± 0.34b | 2.00 ± 0.34ab |
R | 5.00 ± 0.58b | 6.67 ± 0.88ab | 6.00 ± 1.00ab | 8.67 ± 1.20a | 8.67 ± 0.88a |
H' | 1.13 ± 0.14c | 1.31 ± 0.07bc | 1.49 ± 0.10ab | 1.43 ± 0.02ab | 1.66 ± 0.08a |
E | 0.70 ± 0.03b | 0.70 ± 0.06b | 0.86 ± 0.04a | 0.67 ± 0.04b | 0.77 ± 0.00ab |
D | 0.43 ± 0.06a | 0.37 ± 0.05ab | 0.27 ± 0.02bc | 0.36 ± 0.04abc | 0.24 ± 0.02c |
Table 3 Effects of precipitation change on soil properties and plant characteristics in August in a desert steppe (mean ± SE)
指标 Index | 处理 Treatment | ||||
---|---|---|---|---|---|
W1 | W2 | W3 | W4 | W5 | |
pH | 8.52 ± 0.05bc | 8.58 ± 0.04ab | 8.43 ± 0.04c | 8.67 ± 0.05a | 8.66 ± 0.04a |
EC | 89.97 ± 0.88a | 93.37 ± 2.44a | 128.70 ± 18.49a | 289.67 ± 22.93a | 358.00 ± 38.19a |
SOC | 2.96 ± 0.08b | 3.25 ± 0.50ab | 3.34 ± 0.17ab | 3.38 ± 0.24ab | 3.70 ± 0.12a |
TN | 0.48 ± 0.00a | 0.49 ± 0.01a | 0.48 ± 0.01a | 0.43 ± 0.02b | 0.43 ± 0.01b |
TP | 0.34 ± 0.00a | 0.29 ± 0.00b | 0.27 ± 0.01c | 0.28 ± 0.00bc | 0.27 ± 0.00c |
NO3--N | 5.50 ± 0.41a | 5.08 ± 0.76ab | 3.28 ± 0.05b | 5.19 ± 0.91a | 5.81 ± 0.42a |
NH4+-N | 2.91 ± 0.23a | 3.59 ± 0.68a | 5.44 ± 1.12a | 5.71 ± 1.84a | 5.31 ± 3.34a |
AP | 1.56 ± 0.13a | 1.62 ± 0.51a | 1.72 ± 0.28a | 2.14 ± 0.30a | 2.47 ± 0.68a |
SA | 318.41 ± 33.75c | 359.39 ± 41.44bc | 381.78 ± 33.90abc | 434.93 ± 36.46ab | 474.67 ± 30.07a |
UA | 27.85 ± 3.86b | 30.68 ± 0.67b | 30.95 ± 1.96b | 45.34 ± 4.52a | 45.70 ± 4.82a |
PA | 44.58 ± 0.32bc | 40.89 ± 3.01c | 43.88 ± 2.97bc | 49.02 ± 2.42ab | 55.60 ± 1.35a |
MBC | 99.05 ± 9.57ab | 77.05 ± 20.59ab | 46.68 ± 14.32b | 100.24 ± 27.02ab | 108.73 ± 8.91a |
MBN | 48.97 ± 2.28a | 5.90 ± 0.80a | 7.45 ± 1.74a | 15.10 ± 7.95a | 19.91 ± 8.67a |
MBP | 1.76 ± 0.73b | 3.56 ± 0.40a | 1.76 ± 0.76b | 1.14 ± 0.34b | 2.00 ± 0.34ab |
R | 5.00 ± 0.58b | 6.67 ± 0.88ab | 6.00 ± 1.00ab | 8.67 ± 1.20a | 8.67 ± 0.88a |
H' | 1.13 ± 0.14c | 1.31 ± 0.07bc | 1.49 ± 0.10ab | 1.43 ± 0.02ab | 1.66 ± 0.08a |
E | 0.70 ± 0.03b | 0.70 ± 0.06b | 0.86 ± 0.04a | 0.67 ± 0.04b | 0.77 ± 0.00ab |
D | 0.43 ± 0.06a | 0.37 ± 0.05ab | 0.27 ± 0.02bc | 0.36 ± 0.04abc | 0.24 ± 0.02c |
Fig. 5 Fitting relationships of soil respiration rate (SR) with soil temperature (T) and water content (W) across the whole growing season in a desert steppe.
Fig. 6 Variation partitioning of soil respiration rate by environmental factor groups in a desert steppe. Values < 0 are not shown. Data in one circle represent the variation individually explained by the environmental factor groups. Data in the overlapped part of circles represent the variation jointly explained by environmental factor groups. X1 group includes soil temperature, water content, pH, organic carbon, nitrate nitrogen, and ammonium nitrogen content. X2 group includes soil sucrase activity and microbial biomass carbon, nitrogen, phosphorus content. X3 group includes Shannon-Wiener diversity index and Pielou evenness index.
Fig. 7 Structural equation model of soil respiration rate and environmental factors under changing precipitation regimes in a desert steppe. CP, precipitation; PB, plant biomass; R, Patrick richness index; SBP, soil biological properties (sucrase activity, urease activity, phosphatase activity, microbial biomass carbon content); SCP, soil chemical property (pH, electrical conductivity, organic carbon, available phosphorus content); SPP, soil physical property (water content and temperature); SR, soil respiration rate. Black solid and dashed arrows indicate significant (p < 0.05) and insignificant (p > 0.05) path, respectively. Numbers on the arrows are normalized path coefficients (*, p < 0.05; **, p < 0.01; ***, p < 0.001). Model fit summary: χ2 = 5.709, p = 0.457, df = 6; comparative fit index (GFI) = 0.998; root mean square error of approximation (RMSEA) = 0.000; standardized root mean square residual (SRMR) = 0.035.
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