{"title":"豆科植物为基础的农业生态系统N2O排放模式","authors":"B. Nicolardot, Maé Guinet, A. Voisin, C. Hénault","doi":"10.21926/aeer.2302029","DOIUrl":null,"url":null,"abstract":"Legumes provide several ecological services to agroecosystems, but there is a lack of references on services related to N flows for a wide range of legume crops. N2O emissions were measured in two field experiments using a two-year legume-cereal crop sequence. In the first year (2014 and 2016), different legume crops were grown (lupin, pea, fava bean, common bean, soybean, chickpea) and compared to fertilized cereals (barley and sorghum). Once the seeds were harvested and the residues incorporated in the soil, unfertilized wheat was sown and harvested in the second year (2015 and 2017). N2O emissions, as well as soil temperature and moisture, were measured continuously using an automated chamber method during the two years of each experiment. Daily N2O emissions were less than 10 g N-N2O ha-1 d-1, with higher values (ranging from 10 to 90 g N-N2O ha-1 d-1) being measured during exceptionally rainy conditions. Daily N2O emissions were mainly influenced by climatic conditions for field experiments and far less by inorganic N content, except for N-fertilized cereals. For both field experiments, cumulative N2O emissions during legume and cereal pre-crops + fallow period between pre-crop harvest and wheat sowing (1st year) (mean values 365.4 and 318.1 g N-N2O ha-1 for experiment I and II, respectively) were higher than during wheat crop cultivation (2nd year) (155.8 and 101.5 g N-N2O ha-1 for experiment I and II, respectively). For field experiment II, N2O emissions were slightly higher for the N fertilized cereal pre-crops (529.8 and 523.3 g N-N2O ha-1 for barley and sorghum, respectively) compared to legume pre-crops (mean values 380.6 and 417.2 g N-N2O ha-1 for legumes sown in March and May, respectively), while no significant difference was measured for field experiment I. There was no difference in N2O emissions during the cultivation of the different legume species. Furthermore, when wheat was grown after legumes or N fertilized cereals, N2O emissions were comparable for the different experimental treatments with no relation established with the amounts of N present in crop residues or their C: N ratios. Despite the small differences in emissions between N-fertilized cereals and grain legumes, introducing these leguminous species in crop rotation and in these pedoclimatic conditions makes it possible to substitute synthetic N fertilizer and mitigate the greenhouse gases emitted from these cropping systems. However, further research is still needed to clarify and quantify the value of legumes in mitigating and reducing greenhouse gas emissions from cropping systems.","PeriodicalId":198785,"journal":{"name":"Advances in Environmental and Engineering Research","volume":"6 1","pages":"0"},"PeriodicalIF":0.0000,"publicationDate":"2023-04-26","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"N2O Emission Pattern in A Legume-Based Agroecosystem\",\"authors\":\"B. Nicolardot, Maé Guinet, A. Voisin, C. Hénault\",\"doi\":\"10.21926/aeer.2302029\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"Legumes provide several ecological services to agroecosystems, but there is a lack of references on services related to N flows for a wide range of legume crops. N2O emissions were measured in two field experiments using a two-year legume-cereal crop sequence. In the first year (2014 and 2016), different legume crops were grown (lupin, pea, fava bean, common bean, soybean, chickpea) and compared to fertilized cereals (barley and sorghum). Once the seeds were harvested and the residues incorporated in the soil, unfertilized wheat was sown and harvested in the second year (2015 and 2017). N2O emissions, as well as soil temperature and moisture, were measured continuously using an automated chamber method during the two years of each experiment. Daily N2O emissions were less than 10 g N-N2O ha-1 d-1, with higher values (ranging from 10 to 90 g N-N2O ha-1 d-1) being measured during exceptionally rainy conditions. Daily N2O emissions were mainly influenced by climatic conditions for field experiments and far less by inorganic N content, except for N-fertilized cereals. For both field experiments, cumulative N2O emissions during legume and cereal pre-crops + fallow period between pre-crop harvest and wheat sowing (1st year) (mean values 365.4 and 318.1 g N-N2O ha-1 for experiment I and II, respectively) were higher than during wheat crop cultivation (2nd year) (155.8 and 101.5 g N-N2O ha-1 for experiment I and II, respectively). For field experiment II, N2O emissions were slightly higher for the N fertilized cereal pre-crops (529.8 and 523.3 g N-N2O ha-1 for barley and sorghum, respectively) compared to legume pre-crops (mean values 380.6 and 417.2 g N-N2O ha-1 for legumes sown in March and May, respectively), while no significant difference was measured for field experiment I. There was no difference in N2O emissions during the cultivation of the different legume species. Furthermore, when wheat was grown after legumes or N fertilized cereals, N2O emissions were comparable for the different experimental treatments with no relation established with the amounts of N present in crop residues or their C: N ratios. Despite the small differences in emissions between N-fertilized cereals and grain legumes, introducing these leguminous species in crop rotation and in these pedoclimatic conditions makes it possible to substitute synthetic N fertilizer and mitigate the greenhouse gases emitted from these cropping systems. However, further research is still needed to clarify and quantify the value of legumes in mitigating and reducing greenhouse gas emissions from cropping systems.\",\"PeriodicalId\":198785,\"journal\":{\"name\":\"Advances in Environmental and Engineering Research\",\"volume\":\"6 1\",\"pages\":\"0\"},\"PeriodicalIF\":0.0000,\"publicationDate\":\"2023-04-26\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Advances in Environmental and Engineering Research\",\"FirstCategoryId\":\"1085\",\"ListUrlMain\":\"https://doi.org/10.21926/aeer.2302029\",\"RegionNum\":0,\"RegionCategory\":null,\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"\",\"JCRName\":\"\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Advances in Environmental and Engineering Research","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.21926/aeer.2302029","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 0
摘要
豆科植物为农业生态系统提供了几种生态服务,但缺乏关于各种豆科作物氮流相关服务的参考文献。采用为期两年的豆类-谷类作物序列,在两次田间试验中测量了N2O排放量。在第一年(2014年和2016年),种植了不同的豆类作物(罗苹、豌豆、蚕豆、普通豆、大豆、鹰嘴豆),并与施肥的谷物(大麦和高粱)进行了比较。一旦收获种子并将残留物融入土壤,在第二年(2015年和2017年)播种和收获未施肥的小麦。在每次实验的两年时间里,使用自动箱法连续测量N2O排放以及土壤温度和湿度。日N2O排放量小于10 g N-N2O ha-1 d-1,在异常多雨条件下测量到更高的值(范围从10到90 g N-N2O ha-1 d-1)。除施氮谷物外,大田试验日N2O排放主要受气候条件影响,受无机氮含量影响较小。在这两个大田试验中,豆科和谷类作物茬前+茬前收获和小麦播种之间的休耕期(第1年)的累积N2O排放量(试验1和试验2的平均值分别为365.4和318.1 g N-N2O ha-1)高于小麦作物栽培期(第2年)(试验1和试验2的平均值分别为155.8和101.5 g N-N2O ha-1)。在大田试验II中,施氮的谷类预作物(大麦和高粱分别为529.8和523.3 g N-N2O ha-1)的N2O排放量略高于豆类预作物(3月和5月播种的豆类分别为380.6和417.2 g N-N2O ha-1),而在大田试验i中,N2O排放量无显著差异。不同豆科作物种植期间,N2O排放量无差异。此外,当小麦在豆类或施氮谷物之后种植时,不同试验处理的N2O排放量具有可比性,与作物残茬中存在的N量或其C: N比率无关。尽管施氮谷物和豆科谷物之间的排放差异很小,但在这些土壤气候条件下,在轮作中引入这些豆科植物,可以替代合成氮肥,减轻这些种植系统排放的温室气体。然而,仍需要进一步的研究来阐明和量化豆类在缓解和减少种植系统温室气体排放方面的价值。
N2O Emission Pattern in A Legume-Based Agroecosystem
Legumes provide several ecological services to agroecosystems, but there is a lack of references on services related to N flows for a wide range of legume crops. N2O emissions were measured in two field experiments using a two-year legume-cereal crop sequence. In the first year (2014 and 2016), different legume crops were grown (lupin, pea, fava bean, common bean, soybean, chickpea) and compared to fertilized cereals (barley and sorghum). Once the seeds were harvested and the residues incorporated in the soil, unfertilized wheat was sown and harvested in the second year (2015 and 2017). N2O emissions, as well as soil temperature and moisture, were measured continuously using an automated chamber method during the two years of each experiment. Daily N2O emissions were less than 10 g N-N2O ha-1 d-1, with higher values (ranging from 10 to 90 g N-N2O ha-1 d-1) being measured during exceptionally rainy conditions. Daily N2O emissions were mainly influenced by climatic conditions for field experiments and far less by inorganic N content, except for N-fertilized cereals. For both field experiments, cumulative N2O emissions during legume and cereal pre-crops + fallow period between pre-crop harvest and wheat sowing (1st year) (mean values 365.4 and 318.1 g N-N2O ha-1 for experiment I and II, respectively) were higher than during wheat crop cultivation (2nd year) (155.8 and 101.5 g N-N2O ha-1 for experiment I and II, respectively). For field experiment II, N2O emissions were slightly higher for the N fertilized cereal pre-crops (529.8 and 523.3 g N-N2O ha-1 for barley and sorghum, respectively) compared to legume pre-crops (mean values 380.6 and 417.2 g N-N2O ha-1 for legumes sown in March and May, respectively), while no significant difference was measured for field experiment I. There was no difference in N2O emissions during the cultivation of the different legume species. Furthermore, when wheat was grown after legumes or N fertilized cereals, N2O emissions were comparable for the different experimental treatments with no relation established with the amounts of N present in crop residues or their C: N ratios. Despite the small differences in emissions between N-fertilized cereals and grain legumes, introducing these leguminous species in crop rotation and in these pedoclimatic conditions makes it possible to substitute synthetic N fertilizer and mitigate the greenhouse gases emitted from these cropping systems. However, further research is still needed to clarify and quantify the value of legumes in mitigating and reducing greenhouse gas emissions from cropping systems.