Pinshang Xu , Ziheng Zou , Guoliang Zhang , Zhutao Li , Zhaoqiang Han , Davey L. Jones , Jinyang Wang
{"title":"Monitoring, characterization, and mitigation of nitrous oxide emissions from Chinese orchards","authors":"Pinshang Xu , Ziheng Zou , Guoliang Zhang , Zhutao Li , Zhaoqiang Han , Davey L. Jones , Jinyang Wang","doi":"10.1016/j.agee.2025.109925","DOIUrl":null,"url":null,"abstract":"<div><div>Chinese orchards have emerged as emission hotspots of nitrous oxide (N<sub>2</sub>O) due to their high nitrogen (N) inputs. However, unique fertilizer application methods may lead to inaccuracies in monitoring and calculating N<sub>2</sub>O emissions, potentially resulting in overestimations or underestimations. The emission variation among different orchards and the dominant influencing factors also need further clarification. This study summarizes the methods used to monitor and estimate soil N<sub>2</sub>O emissions from orchards in China. It underscores the critical importance of appropriately arranging sampling boxes by considering fertilized and unfertilized areas and the range of irrigation radiation. Accurately scaling up chamber measurements to the landscape level requires precise calculations of these areas. Corrections must account for the spatial distribution of water, N, and N<sub>2</sub>O emissions in irrigated orchards. Random forest and structural equation modeling results indicate that N input is the primary factor influencing N<sub>2</sub>O emissions, while climate, soil characteristics, and other field management also play significant roles. Significant variations in emissions among different orchard types were observed, primarily attributed to differences in N input and fertilization methods. Average N<sub>2</sub>O emissions from peach and grape orchards (7.21 vs. 8.98 kg N ha<sup>−1</sup>) are significantly greater than those from other orchards (3.02–4.87 kg N ha<sup>−1</sup>). Furthermore, N fertilization exacerbated the disparity in N<sub>2</sub>O emissions between evergreen and deciduous orchards (4.02 vs. 6.06 kg N ha<sup>−1</sup>). Three climate-smart strategies have been identified to mitigate the hotspot issue of N<sub>2</sub>O emissions from Chinese orchards and promote sustainable orchard development. In conclusion, with policy guidance and improved field management, China is well-positioned to lead in climate-smart orchard management practices and contribute to global climate change mitigation. Further research and innovation in orchard systems management will be crucial in achieving carbon neutrality and ensuring the long-term sustainability of orchard systems.</div></div>","PeriodicalId":7512,"journal":{"name":"Agriculture, Ecosystems & Environment","volume":"395 ","pages":"Article 109925"},"PeriodicalIF":6.4000,"publicationDate":"2025-08-22","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Agriculture, Ecosystems & Environment","FirstCategoryId":"97","ListUrlMain":"https://www.sciencedirect.com/science/article/pii/S0167880925004578","RegionNum":1,"RegionCategory":"农林科学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"AGRICULTURE, MULTIDISCIPLINARY","Score":null,"Total":0}
引用次数: 0
Abstract
Chinese orchards have emerged as emission hotspots of nitrous oxide (N2O) due to their high nitrogen (N) inputs. However, unique fertilizer application methods may lead to inaccuracies in monitoring and calculating N2O emissions, potentially resulting in overestimations or underestimations. The emission variation among different orchards and the dominant influencing factors also need further clarification. This study summarizes the methods used to monitor and estimate soil N2O emissions from orchards in China. It underscores the critical importance of appropriately arranging sampling boxes by considering fertilized and unfertilized areas and the range of irrigation radiation. Accurately scaling up chamber measurements to the landscape level requires precise calculations of these areas. Corrections must account for the spatial distribution of water, N, and N2O emissions in irrigated orchards. Random forest and structural equation modeling results indicate that N input is the primary factor influencing N2O emissions, while climate, soil characteristics, and other field management also play significant roles. Significant variations in emissions among different orchard types were observed, primarily attributed to differences in N input and fertilization methods. Average N2O emissions from peach and grape orchards (7.21 vs. 8.98 kg N ha−1) are significantly greater than those from other orchards (3.02–4.87 kg N ha−1). Furthermore, N fertilization exacerbated the disparity in N2O emissions between evergreen and deciduous orchards (4.02 vs. 6.06 kg N ha−1). Three climate-smart strategies have been identified to mitigate the hotspot issue of N2O emissions from Chinese orchards and promote sustainable orchard development. In conclusion, with policy guidance and improved field management, China is well-positioned to lead in climate-smart orchard management practices and contribute to global climate change mitigation. Further research and innovation in orchard systems management will be crucial in achieving carbon neutrality and ensuring the long-term sustainability of orchard systems.
中国果园因其高氮输入而成为一氧化二氮(N2O)排放热点。然而,独特的施肥方法可能导致监测和计算N2O排放量的不准确,可能导致高估或低估。不同果园间的排放差异及其主导影响因素也有待进一步明确。本文综述了中国果园土壤N2O排放监测与估算方法。它强调了通过考虑施肥和未施肥区域以及灌溉辐射范围来适当安排取样箱的关键重要性。将室内测量精确地扩大到景观水平需要对这些区域进行精确计算。修正必须考虑到灌溉果园中水、氮和氧化亚氮排放的空间分布。随机森林模型和结构方程模型结果表明,氮素输入是影响N2O排放的主要因素,气候、土壤特征和其他田间管理也起着重要作用。不同果园类型间碳排放差异显著,主要归因于氮素输入和施肥方式的差异。桃园和葡萄园N2O平均排放量(7.21 vs. 8.98 kg N ha−1)显著高于其他果园(3.02-4.87 kg N ha−1)。此外,施氮加剧了常绿与落叶果园N2O排放差异(4.02 vs 6.06 kg N ha−1)。为缓解我国果园N2O排放的热点问题,促进果园可持续发展,提出了三种气候智能型策略。总之,通过政策指导和改进田间管理,中国完全有能力引领气候智能型果园管理实践,并为减缓全球气候变化作出贡献。果园系统管理的进一步研究和创新对于实现碳中和和确保果园系统的长期可持续性至关重要。
期刊介绍:
Agriculture, Ecosystems and Environment publishes scientific articles dealing with the interface between agroecosystems and the natural environment, specifically how agriculture influences the environment and how changes in that environment impact agroecosystems. Preference is given to papers from experimental and observational research at the field, system or landscape level, from studies that enhance our understanding of processes using data-based biophysical modelling, and papers that bridge scientific disciplines and integrate knowledge. All papers should be placed in an international or wide comparative context.