Does spontaneous cover crop increase the stocks of soil organic carbon and nitrogen in commercial olive orchard?

IF 6.1 1区 农林科学 Q1 SOIL SCIENCE Soil & Tillage Research Pub Date : 2024-07-24 DOI:10.1016/j.still.2024.106237
Evangelina Pareja-Sánchez , Julio Calero , Roberto García-Ruiz
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Abstract

Management practices in the inter-row area of olive orchards are undergoing significant transformations. Current regulations and recommendations are increasingly advocating the implementation of temporary spontaneous cover crops (TSCV) mainly to reduce erosion. Existing research has predominantly focused on evaluating the effectiveness of TSCV in mitigating soil erosion in olive orchards, with limited attention given to carbon (C) cycling, despite the potential of TSCV for contributing to the removal of atmospheric CO2 and in the reduction of eroded carbon. Moreover, the limited number of studies on the effects of TSCV on C cycling have been confined to a few experimental sites and at the short term. This study aimed to assess the potential of TSCV to enhance carbon sequestration and nitrogen retention in rainfed commercial olive orchards under semi-arid conditions. To achieve this, we evaluated the annual aboveground organic carbon input due to TSCV, as well as the stocks of soil organic (SOC) and inorganic (SIC) carbon and total N (STN) in 24 commercial olive groves with calcareous Regosols and calcium Cambisols as the predominant soil types that have implemented TSCV for at least the last 8 years. These were compared with 24 comparable groves with bare soil (BS). Net aboveground annual carbon and CO2 fixation of the TSCV averaged 125.7 kg C ha−1 y−1 and 460 kg CO2 ha−1 y−1, respectively, which are figures relatively low mainly due to the low area covered by the TSCV. After eight years of implementing TSCV, the SOC stocks increased by an average of 2.03 Mg C ha−1 (in the top 30 cm of soil) compared to BS olive orchards. Moreover, SOC content of unprotected (>250 µm) and physically protected (53–250 µm) fractions were 82 and 38 % higher in the TSCV olive farms. Although there was a tendency of lower SIC content in TSCV olive orchards, differences were not significant. The STN content and the potentially mineralizable nitrogen in TSCV farms were on average 26 % and 77 % higher than in BS olive orchards. These findings underscore the potential of TSCV for organic carbon accumulation and nitrogen retention in the soil, contributing to climate change mitigation and soil fertility enhancement. Increasing vegetation coverage and productivity can enhance their effectiveness.

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自发覆盖作物是否会增加商业橄榄园的土壤有机碳和氮储量?
橄榄园行间区域的管理方法正在发生重大转变。目前的法规和建议越来越多地提倡实施临时自发覆盖作物(TSCV),主要是为了减少水土流失。现有的研究主要集中在评估临时自生覆盖作物在减轻橄榄园土壤侵蚀方面的效果,而对碳(C)循环的关注有限,尽管临时自生覆盖作物具有清除大气中二氧化碳和减少被侵蚀碳的潜力。此外,关于 TSCV 对碳循环影响的研究数量有限,而且仅限于少数几个实验点和短期研究。本研究旨在评估 TSCV 在半干旱条件下的雨水灌溉商业橄榄园中提高固碳和固氮的潜力。为此,我们评估了 24 个以钙质 Regosols 和钙质 Cambisols 为主要土壤类型且至少在过去 8 年中实施了 TSCV 的商业橄榄园每年因 TSCV 而产生的地上有机碳输入量,以及土壤有机碳(SOC)、无机碳(SIC)和总氮(STN)的存量。这些橄榄园与 24 个裸露土壤(BS)的同类橄榄园进行了比较。TSCV每年的地上碳和二氧化碳净固定量平均分别为125.7千克碳公顷年和460千克二氧化碳公顷年,这两个数字相对较低,主要是因为TSCV覆盖的面积较小。实施 TSCV 八年后,与 BS 橄榄园相比,SOC 储量平均增加了 2.03 兆克 C 公顷(土壤顶部 30 厘米)。此外,在 TSCV 橄榄园中,未受保护部分(>250 微米)和物理保护部分(53-250 微米)的 SOC 含量分别高出 82% 和 38%。虽然 TSCV 橄榄园的 SIC 含量有降低的趋势,但差异并不显著。TSCV 橄榄园的 STN 含量和潜在矿化氮分别比 BS 橄榄园平均高出 26% 和 77%。这些发现强调了TSCV在土壤有机碳积累和氮保持方面的潜力,有助于减缓气候变化和提高土壤肥力。提高植被覆盖率和生产力可以增强其效果。
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来源期刊
Soil & Tillage Research
Soil & Tillage Research 农林科学-土壤科学
CiteScore
13.00
自引率
6.20%
发文量
266
审稿时长
5 months
期刊介绍: Soil & Tillage Research examines the physical, chemical and biological changes in the soil caused by tillage and field traffic. Manuscripts will be considered on aspects of soil science, physics, technology, mechanization and applied engineering for a sustainable balance among productivity, environmental quality and profitability. The following are examples of suitable topics within the scope of the journal of Soil and Tillage Research: The agricultural and biosystems engineering associated with tillage (including no-tillage, reduced-tillage and direct drilling), irrigation and drainage, crops and crop rotations, fertilization, rehabilitation of mine spoils and processes used to modify soils. Soil change effects on establishment and yield of crops, growth of plants and roots, structure and erosion of soil, cycling of carbon and nutrients, greenhouse gas emissions, leaching, runoff and other processes that affect environmental quality. Characterization or modeling of tillage and field traffic responses, soil, climate, or topographic effects, soil deformation processes, tillage tools, traction devices, energy requirements, economics, surface and subsurface water quality effects, tillage effects on weed, pest and disease control, and their interactions.
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