Integrated crop-livestock farms have higher topsoil nitrogen and carbon than crop-only farms in Chilean Mediterranean climate volcanic soils

IF 6.1 1区 农林科学 Q1 AGRICULTURE, MULTIDISCIPLINARY Agricultural Systems Pub Date : 2024-11-08 DOI:10.1016/j.agsy.2024.104172
Leah L.R. Renwick , Ayleen Celedón , Francisco Nájera , Juan-Pablo Fuentes Espoz , Daniela Celedón , Claudia Arellano , Osvaldo Salazar
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Abstract

Context

Crop-livestock reintegration could reduce the environmental footprint of decoupled crop and livestock production related to biogeochemical cycles. Previous experiments showed that replacing fallow periods in annual crop rotations with grazed cover crops increases total nitrogen (N) and organic carbon (SOC), based on topsoil sampling and stocks compared by equivalent soil depth. Stock comparisons based on topsoil sampling or equivalent soil depth, rather than whole-profile sampling or equivalent soil mass, can erroneously report stock gains that have not occurred. Evidence of crop-livestock integration effects on commercial farms is needed.

Objective

This study assessed on-farm if winter grass forages and beef cattle grazing in annual crop rotations lead to greater soil total N and SOC to a soil depth of 1 m.

Methods

We sampled soil at eight paired commercial fields, four integrated crop-livestock (ICL) fields with grazed or ungrazed winter forage (annual ryegrass, oat) in the crop rotation (cereals, grain legumes, industrial crops), and four neighboring fields with winter fallow in the rotation, in volcanic soils in Ñuble Region, central-southern Chile, in fall 2022 and 2023. In each field, 10 soil cores were sampled from a 1 ha plot and separated into four depth layers (0–15 cm, 15–30 cm, 30–60 cm, and 60–100 cm). We quantified soil total N and SOC concentrations and stocks, on an equivalent soil mass basis, and soil texture throughout the soil profile.

Results and conclusions

ICL sites had 10 % higher total N (+0.05 % N) and 8 % higher SOC concentrations (+0.5 % SOC) compared to paired non-ICL sites in the top 15 cm soil layer. The topsoil layer at ICL sites had 11 % higher N (+0.37 Mg N ha−1) and 9 % higher SOC (+3.9 Mg SOC ha−1) stocks, based on an equivalent soil mass. Cumulative stocks below 15 cm to a depth of 1 m were similar between ICL and non-ICL sites. Across the 1 m soil profile, 52 % and 53 % of N and SOC stocks were below 30 cm depth.

Significance

We provided on-farm evidence suggesting that integrating non-leguminous winter forages and grazing into annual crop rotations can retain N and store SOC in topsoil, with relevance to land managers and decision-makers who seek to build soil fertility and health through biodiversity and reduce N fertilizer use, though further research is recommended. Sampling soil to at least 60 cm depth can help capture management effects on N and SOC and quantify deeper N retention and SOC storage.

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在智利地中海气候的火山土壤中,作物-牲畜综合农场的表土氮含量和碳含量均高于纯作物农场
背景作物-牲畜的重新整合可以减少作物和牲畜生产脱钩对生物地球化学循环造成的环境影响。之前的实验表明,根据表土取样和等效土壤深度的储量比较,用放牧覆盖作物取代一年生作物轮作中的休耕期可增加总氮(N)和有机碳(SOC)。基于表土取样或等效土壤深度而非全剖面取样或等效土壤质量进行的储量比较,可能会错误地报告并未发生的储量增加。本研究在农场评估了冬季牧草和肉牛在一年生作物轮作中的放牧是否会增加土壤中 1 米深度的总氮和 SOC。方法我们于 2022 年秋季和 2023 年秋季在智利中南部尼布勒大区的火山土壤中的八块成对的商业田地、四块作物-牲畜(ICL)综合田地(轮作(谷物、谷物豆类、工业作物)中放牧或未放牧冬季牧草(一年生黑麦草、燕麦))以及四块相邻的轮作中冬季休耕的田地进行了土壤采样。在每块田地中,我们从 1 公顷的地块中采集了 10 个土壤样本,并将其分成四个深度层(0-15 厘米、15-30 厘米、30-60 厘米和 60-100 厘米)。我们以等效土壤质量为基础,对整个土壤剖面的土壤全氮和 SOC 浓度及储量以及土壤质地进行了量化。根据等效土壤质量计算,ICL 地点表土层的氮储量(+0.37 兆克氮公顷-1)和 SOC 储量(+3.9 兆克 SOC 公顷-1)分别高出 11% 和 9%。15 厘米以下至 1 米深处的累积储量在 ICL 与非 ICL 地点之间相似。我们提供的农场证据表明,将非豆科冬季牧草和放牧与一年生作物轮作相结合,可以在表层土壤中保留氮并储存SOC,这对寻求通过生物多样性提高土壤肥力和健康水平并减少氮肥使用量的土地管理者和决策者具有重要意义,但建议开展进一步研究。对至少 60 厘米深的土壤进行取样,有助于捕捉管理对氮和 SOC 的影响,并量化更深层的氮保留和 SOC 储存。
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来源期刊
Agricultural Systems
Agricultural Systems 农林科学-农业综合
CiteScore
13.30
自引率
7.60%
发文量
174
审稿时长
30 days
期刊介绍: Agricultural Systems is an international journal that deals with interactions - among the components of agricultural systems, among hierarchical levels of agricultural systems, between agricultural and other land use systems, and between agricultural systems and their natural, social and economic environments. The scope includes the development and application of systems analysis methodologies in the following areas: Systems approaches in the sustainable intensification of agriculture; pathways for sustainable intensification; crop-livestock integration; farm-level resource allocation; quantification of benefits and trade-offs at farm to landscape levels; integrative, participatory and dynamic modelling approaches for qualitative and quantitative assessments of agricultural systems and decision making; The interactions between agricultural and non-agricultural landscapes; the multiple services of agricultural systems; food security and the environment; Global change and adaptation science; transformational adaptations as driven by changes in climate, policy, values and attitudes influencing the design of farming systems; Development and application of farming systems design tools and methods for impact, scenario and case study analysis; managing the complexities of dynamic agricultural systems; innovation systems and multi stakeholder arrangements that support or promote change and (or) inform policy decisions.
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