在向保护性农业过渡的过程中,通过种植豆科覆盖作物减少最初的棉花产量损失--来自贝宁北部的证据

IF 6.1 1区 农林科学 Q1 SOIL SCIENCE
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引用次数: 0

摘要

贝宁北部一直在大力推广保护性农业(CA),以维持棉花(Gossypium hirsutum L.)种植系统向生态农业的过渡。然而,农民对保护性农业的采用有限,这通常归因于向保护性农业过渡期间的初始产量损失以及作物生物量利用方面的权衡。在此,我们评估了该地区推广的基于 CA 的不同种植系统对棉花/玉米(Zea mays L.)三年轮作中水生产力和棉花产量的影响。我们评估了三种 CA 方案,它们结合了不同程度的土壤扰动和覆盖,并引入了覆盖作物以减轻生物量权衡。从 2017 年到 2019 年,在该地区的主要土壤类型 Haplic Lixisols 下,对直接播种 (DS)、带状耕作 (ST) 和直接播种地膜覆盖种植系统 (DMC) 与传统耕作 (CT) 进行了比较。两种豆科植物 Stylosanthes guianensis (Aubl.) Sw. 和 Crotalaria retusa L. 在 ST 和 DMC 下作为覆盖作物与玉米一起种植。实验采用随机区组设计,共设六个重复。经过 2-3 年的 DMC 后,棉花产量相对于 CT 的优势从 5% 增加到 7%。在 2018 年和 2019 年,DS 的棉花产量分别减少了 11% 和 26%。ST 处理的产量优势从 2017 年的 8% 变为 2019 年的 20%。与 ST 和 DS 处理相比,DMC 和 CT 处理的棉铃重相似且最高。各处理在每株棉铃数方面没有显著差异。与 CT、ST 和 DS 相比,DMC 处理地块上部 30 厘米深度的土壤储水量和水分利用效率(WUE)最高。在 28 天的活性植株期(播种后 34 至 62 天之间),DMC 的籽棉水分利用效率为 0.11 千克/公顷-1 毫米-1,而 DS、CT 和 ST 分别为 0.08、0.07 和 0.04 千克/公顷-1 毫米-1。DMC 在提高水分生产率方面的表现可以作为提高贝宁北部农民采用率的一个论据,因为这些农民面临着越来越多的天气变化,而在完全 DMC 条件下,并没有观察到通常与早期向 CA 过渡相关的产量损失。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Reducing initial cotton yield penalties in a transition to conservation agriculture through legume cover crop cultivation – evidence from Northern Benin
Much effort has been spent on promoting conservation agriculture (CA) in Northern Benin to sustain the transition of cotton (Gossypium hirsutum L.) cropping systems toward agroecology. However, its limited adoption by farmers is often ascribed to initial yield penalties during the transition to CA and to trade-offs around crop biomass use. Here, we assess the effect of different CA-based cropping systems promoted in the region on water productivity and cotton yield in a three-year cotton/maize (Zea mays L.) crop rotation during the initial transition phase to CA. Three CA options were assessed combining different levels of soil disturbance and cover, and introducing cover crops to alleviate the biomass trade-offs. Direct seeding (DS), strip tillage (ST), and direct seeding mulched-based cropping systems (DMC) were compared with conventional tillage (CT) from 2017 to 2019 under a dominant soil type in the region, Haplic Lixisols. Two legume species, Stylosanthes guianensis (Aubl.) Sw. and Crotalaria retusa L. were grown as cover crops with maize under ST and DMC. The experiment followed a randomized block design comprising six replicates. After 2–3 years of DMC, the cotton yield advantage with respect to CT increased from 5 % to 7 %. Cotton yield penalties of respectively 11 % in 2018 and 26 % in 2019 were found for DS. ST treatment went from a yield advantage of 8 % in 2017 to a yield penalty of 20 % in 2019. The DMC and CT treatments gave similar and highest boll weights compared to the ST and DS treatments. The treatments had no significant difference regarding the number of bolls per plant. Soil water storage in the upper 30 cm depth and water use efficiency (WUE) were the highest in the plots with the DMC treatment compared to CT, ST, and DS. At 28 days of active vegetative stage (between 34 and 62 days after sowing), the WUE of seed cotton was 0.11 kg ha−1 mm−1 under DMC, while it was 0.08, 0.07, and 0.04 kg ha−1 mm−1 under DS, CT, and ST, respectively. The performance of DMC at increasing water productivity could be an argument to improve adoptability by farmers in northern Benin who are facing increased weather variability, given that the yield penalties often associated with early transitions to CA were not observed here with full DMC.
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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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