极端降雨条件下淹水对农田土壤有机碳、可溶性有机碳的影响

Effects of flooding on soil organic carbon and dissolved organic carbon under extreme rainstorm

  • 摘要: 随着气候变化的日益加剧, 极端降雨事件的发生更为频繁, 但目前针对极端暴雨对土壤有机碳(SOC)及其不同组分的影响还需更深入地研究。本研究以河南省“7.20”极端降雨事件为契机, 选择暴雨事件发生后未淹水(CK)、淹水不超过1个月(Y1)及淹水超过2个月(Y2) 3种不同淹水时长的农田为研究对象, 探讨了极端暴雨事件对0~100 cm土层深度内SOC、可溶性有机碳(DOC)的影响及其主要影响因素。研究结果发现: 1)极端暴雨事件发生后, 农田SOC与DOC随淹水时长的变化呈现不同的变化规律, SOC表现为淹水农田整体高于未淹水农田, 且40 cm以下土层增加比例高于40 cm以上土层。0~100 cm土层内SOC含量CK为3.41~14.25 g∙kg−1, Y1为5.45~18.11 g∙kg−1, Y2为4.68~15.15 g∙kg−1, 随着淹水时长的增加, SOC呈先增加后降低的趋势; 0~100 cm土层内DOC含量CK为414.19~580.39 mg∙kg−1, Y1为327.99~874.19 mg∙kg−1, Y2为242.34~301.93 mg∙kg−1; 随着淹水时长的增加, DOC在0~40 cm土层表现为先增加后降低的趋势, 40 cm以下土层则表现为逐渐降低的趋势, 其中40~60 cm和80~100 cm土层DOC含量CK显著高于Y2。2)极端暴雨事件后, 不同淹水时长下农田SOC和DOC垂直剖面上的分布规律存在差异: 随着土层深度的增加, SOC均呈降低趋势; DOC在CK处理表现为先升高后降低, 其中10~20 cm土层DOC含量最高, Y1的DOC整体表现为随土层深度的增加而降低, Y2的DOC在0~100 cm土层内变化趋势不明显。3)土壤水分能够显著影响SOC及DOC/SOC, 但与DOC之间未见显著回归关系, 土壤总碳、总磷、总氮等养分含量对SOC、DOC及DOC/SOC存在显著的影响, pH和电导率变化与SOC和DOC的分布未见显著相关性。

     

    Abstract: Extreme rainfall events are occurring more frequently with the aggravation of climate change. Further research is required on the effects of extreme rainstorms on soil organic carbon (SOC) and its components. In this study, we took the “7.20” extreme rainfall event in Henan Province as an opportunity. Three types of farmland with different flooding durations, including non-flooded (CK), flooded for less than 1 month (Y1), and flooded for more than 2 months (Y2) after the rainstorm event, were selected to explore the impacts of extreme rainfall events on SOC, dissolved organic carbon (DOC), and their main influencing factors at 0–100 cm soil depth. The results showed that: 1) After the extreme rainfall event, the changes in SOC and DOC with the duration of flooding presented different rules. Overall, the SOC in the flooded farmland was higher than that in the non-flooded farmland, and the increasing proportion of the soil layer below 40 cm was higher than that in the soil layer above 40 cm. The content of SOC in 0−100 cm soil layer was 3.41−14.25 g∙kg−1 under CK, 5.45−18.11 g∙kg−1 under Y1, and 4.68−15.15 g∙kg−1 under Y2. As the waterlogging duration increased, SOC in the farmland first increased and then decreased. The content of DOC in 0−100 cm soil layer was 414.19−580.39 mg∙kg−1 under CK, 327.99−874.19 mg∙kg−1 under Y1, and 242.34−301.93 mg∙kg−1 under Y2. As the waterlogging duration increased, the DOC showed a trend of first increasing and then decreasing in the 0–40 cm layer, while showing a gradually decreasing trend below the 40 cm layer. The DOC content of CK was significantly higher than that of Y2 in 40–60 cm and 80–100 cm soil layers. 2) Differences were noted in the distribution patterns of SOC and DOC in the vertical profiles of the farmland under different waterlogging durations following extreme rainfall events. With an increase in soil depth, SOC showed a decreasing trend; the DOC in CK showed a trend of first increasing and then decreasing, with the highest content of DOC in the 10–20 cm layer. The DOC in Y1 showed an overall decreasing trend with increasing soil depth, while the changing trend of DOC in Y2 was not obvious within the 0−100 cm soil layer. 3) Soil moisture significantly affected SOC and DOC/SOC; however, no significant regression relationship with DOC was observed. The content of soil nutrients, such as total carbon, total phosphorus, and total nitrogen have significant effects on SOC, DOC, and DOC/SOC. No significant correlation was noted between the changes in pH, electrical conductivity, and the distribution of SOC and DOC.

     

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