Soil water balance in response to rainfall variability over a dammed valley farmland in the Chinese Loess Plateau

IF 7 2区 环境科学与生态学 Q1 ENVIRONMENTAL SCIENCES
Han Zheng , Jintao Bai , Panpan Niu , Tao Peng , Zhao Jin , Han Bao , Syeda Alveena Fatima Naqvi , Yijing Guan
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Abstract

The dammed valley farmlands created by a mega land consolidation project are crucial in combating land degradation and sustaining food security in the Chinese Loess Plateau. Understanding the response of soil water balance to rainfall variability is essential for the effective water resources management in water scarcity regions facing global climate change. Based on continuous in situ 3-m soil water profile beneath a dammed valley maize farmland, the Hydrus-1D model was calibrated and then employed to simulate the soil water movement and water budgets during two maize growing seasons with contrasting hydrological conditions in 2019 (drought year) and 2020 (normal year). Results showed that the Hydrus-1D model could accurately depict the soil water dynamics at different depths during the two growing seasons. The simulated soil water storage changes (ΔS) and actual evapotranspiration (ET) also showed good agreement with the ΔS from soil water monitoring data and ET from eddy covariance method, respectively. The simulated data indicated that the maximum infiltration depth of rainfall (P) was 100 cm and 150 cm in 2019 and 2020, respectively. The soil water recharge from groundwater by capillary rise varied significantly with crop phenology and water availability, but with close sums during the two growing seasons (45.24 mm and 34.15 mm). ET dominated the soil water consumption for both years, with the ratio of ET to P of 0.98 and 0.73 during the growing seasons of 2019 and 2020, respectively. The simulated ΔS was pronouncedly lower in the drought year (51.79 mm) compared with the normal year (147.53 mm), representing 16.5 % and 30.3 % of the total growing-season P, respectively. The simulated deep drainage was 20.18 mm in 2020, but this value was reduced to zero in 2019. This research could deepen our understanding on the impacts of rainfall variability on soil water balance in the water-limited agricultural regions.
黄土高原坝谷农田土壤水分平衡对降雨变率的响应
在中国黄土高原,大型土地整理工程形成的河谷农田对防治土地退化和维持粮食安全至关重要。了解土壤水分平衡对降雨变率的响应,对于面临全球气候变化的缺水地区进行有效的水资源管理至关重要。基于坝谷玉米农田3-m连续原位土壤水分剖面,对Hydrus-1D模型进行了标定,模拟了2019年(干旱年)和2020年(正常年)两个玉米生长季节的土壤水分运动和水分收支。结果表明,Hydrus-1D模型能较准确地描述两个生长季节不同深度的土壤水分动态。模拟的土壤储水量变化(ΔS)和实际蒸散发(ET)也分别与土壤水分监测资料的ΔS和涡动相关法的ET具有较好的一致性。模拟数据表明,2019年和2020年降水最大入渗深度(P)分别为100 cm和150 cm。随着作物物候和水分有效性的不同,土壤地下水补给量的毛管上升变化显著,但两个生长季节的总和相近(45.24 mm和34.15 mm)。蒸散发在土壤水分消耗中占主导地位,2019年和2020年生长季蒸散发与土壤水分消耗的比值分别为0.98和0.73。模拟的ΔS在干旱年(51.79 mm)明显低于正常年(147.53 mm),分别占生长季总P的16.5%和30.3%。2020年模拟深排水为20.18 mm, 2019年该数值降为零。本研究可加深我们对水资源限制农业区降雨变率对土壤水分平衡影响的认识。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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来源期刊
Ecological Indicators
Ecological Indicators 环境科学-环境科学
CiteScore
11.80
自引率
8.70%
发文量
1163
审稿时长
78 days
期刊介绍: The ultimate aim of Ecological Indicators is to integrate the monitoring and assessment of ecological and environmental indicators with management practices. The journal provides a forum for the discussion of the applied scientific development and review of traditional indicator approaches as well as for theoretical, modelling and quantitative applications such as index development. Research into the following areas will be published. • All aspects of ecological and environmental indicators and indices. • New indicators, and new approaches and methods for indicator development, testing and use. • Development and modelling of indices, e.g. application of indicator suites across multiple scales and resources. • Analysis and research of resource, system- and scale-specific indicators. • Methods for integration of social and other valuation metrics for the production of scientifically rigorous and politically-relevant assessments using indicator-based monitoring and assessment programs. • How research indicators can be transformed into direct application for management purposes. • Broader assessment objectives and methods, e.g. biodiversity, biological integrity, and sustainability, through the use of indicators. • Resource-specific indicators such as landscape, agroecosystems, forests, wetlands, etc.
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