中国农业科学 ›› 2020, Vol. 53 ›› Issue (13): 2691-2702.doi: 10.3864/j.issn.0578-1752.2020.13.017

• 退耕地恢复技术与原理 • 上一篇    下一篇

草甸草原区退耕地的牧草-水分-氮肥耦合机制

李达1,方华军2,王笛1,徐丽君3(),唐雪娟3,辛晓平3,聂莹莹3,乌仁其其格4   

  1. 1白城市畜牧科学研究院/呼伦贝尔草原生态系统国家野外科学观测研究站/国家牧草产业技术体系白城站,吉林白城137000
    2中国科学院地理科学与资源研究所生态系统观测与模拟重点实验室,北京100101
    3中国农业科学院农业资源与农业区划研究所/呼伦贝尔草原生态系统国家野外科学观测研究站,北京100081
    4呼伦贝尔学院/内蒙古自治区草甸草原生态系统与全球变化重点实验室,内蒙古呼伦贝尔021800
  • 收稿日期:2019-09-22 接受日期:2019-12-26 出版日期:2020-07-01 发布日期:2020-07-16
  • 通讯作者: 徐丽君
  • 作者简介:李达,E-mail: 547273612@qq.com。
  • 基金资助:
    国家重点研发计划(2016YFC0500603);国家自然科学基金项目(417018);国家现代农业产业技术体系建设专项(Cars-34)

Coupling Mechanism of Herbage-Water-Nitrogen Fertilizer in Abandoned Farmland in Meadow Steppe

LI Da1,FANG HuaJun2,WANG Di1,XU LiJun3(),TANG XueJuan3,XIN XiaoPing3,NIE YingYing3,Wuren qiqige4   

  1. 1Institute of Animal Husbandry Science of Baicheng/Hulunber Grassland Ecosystem Observation and Research Station/National Forage Industry Technology System Baicheng Station, Baicheng 137000, Jilin
    2 Key Laboratory of Ecosystem Network Observation and Modeling, Institute of Geographical Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing 100101
    3Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences/Hulunber Grassland Ecosystem Observation and Research Station, Beijing 100081
    4 Hulunber University/Key Laboratory of Meadow Grassland Ecosystem and Global Change in Inner Mongolia Autonomous Region, Hulunber 021800, Inner Mongolia
  • Received:2019-09-22 Accepted:2019-12-26 Online:2020-07-01 Published:2020-07-16
  • Contact: LiJun XU

摘要:

【目的】 通过在呼伦贝尔建植不同种植模式的人工草地,研究补水、施氮和牧草类型3个因素对人工草地群落生物量、植物营养成分和土壤质量的影响,旨在揭示呼伦贝尔地区退耕地人工草地的水肥耦合机制,筛选建植管理的最优模式。【方法】 试验在呼伦贝尔草原生态系统国家野外科学观测研究站进行,2016年6月6日试验开始,设置3个因素试验,即牧草类型(Pasture)、施氮水平(Nitrogen)和补水处理(Irrigation)。牧草类型设紫花苜蓿单播(P1)、无芒雀麦单播(P2)、紫花苜蓿无芒雀麦1﹕1混播(P3)3个处理;施氮水平设不施氮(N0)、低氮(N1:75 kgN·hm-2·a-1)和高氮(N2:150 kgN·hm-2·a-1)3个水平,每年追施氮肥(化学纯尿素)两次分别于成苗(返青)期和分蘖期撒施;补水设不补水(I0)和补水(I1)两个水平,每年6、7、8月补水3次,补水20 mm·m-2。重复4次,共计72个试验小区,每个试验小区面积7 m×10 m,行距1 m。在2016、2017年测定草地生物量、营养成分(植物粗蛋白、中性洗涤纤维和酸性洗涤纤维)以及土壤养分(土壤全氮、有机碳和pH)。【结果】 (1)播种当年(2016年)的产量对(N)、(I)、(P)和(P×I)等试验因素的响应均达到显著水平(P<0.05),2017年两次测定的产量对(N)、(P)、(P×I)、(P×N)、(N×I×P)等试验因素的响应均达到显著水平(P<0.05),并且混播(P3)在不补水(I0)条件下低氮(N1)处理的产量显著高于其余处理组(P<0.05),平均达到17 801.19 kg·hm-2。(2)2016年和2017年的粗蛋白(CP)含量均表现为P1处理>P3处理>P2处理,2016年P1、P2和P3处理在补水条件相同时均表现为CP含量随着氮水平增加而增加,其中P1N2I0显著高于P1N0I0、P1N1I0 、P1N1I1P<0.05),达到最大(19.08%);2017年P3在I0条件下N1水平的粗蛋白(CP)含量(15.12%)显著高于N0P<0.05)。(3)施氮和补水均倾向于促使土壤有机碳(SOC)含量负增长,全氮(TN)含量正增长,pH值负增长,其中表层土壤SOC增长量苜蓿和无芒雀麦显著高于混播(P<0.05),表层土壤全氮(TN)增长量苜蓿显著高于无芒雀麦和混播(P<0.05)。2016年表层和亚表层的土壤碳氮比(C/N)均高于2017年,表层平均高出17.39%,亚表层平均高出15.18%,表层土壤碳氮比的变化更为明显,其中表层土壤碳氮比2016年P1N0I1处理最高,为8.15,2017年P1N2I0处理最高,为5.67,亚表层土壤碳氮比2016年P1N2I1处理最高,为6.36,2017年P3N2I1处理最高,为5.67。【结论】 在呼伦贝尔退耕人工草地在播种第二年,牧草-水分-氮肥的耦合作用对草地生物量具有显著影响,水氮耦合具有一定促进牧草的养分积累的协同效应,其中建植豆-禾混播草地最有利于提高牧草的生物量与营养品质。人工草地的建植会导致C/N降低,土壤品质下降,在不同牧草类型、补水及施氮水平下均会表现出0-20 cm土层SOC含量、pH值的降低以及土壤TN含量的上升,表明土壤出现酸化现象,豆-禾混播土壤pH值降低幅度小于单播,而高氮和补水会明显加剧土壤pH值的降低。

关键词: 人工草地, 施氮, 补水, 豆-禾牧草混播, 群落生物量, 土壤养分, 呼伦贝尔

Abstract:

【Objective】 The study was to investigate the effects of three factors, including water replenishment, nitrogen application, and pasture type, on the biomass, plant nutrient composition and soil quality of artificial grassland communities by planting artificial grassland with different planting patterns of Hulunber, and to reveal the retreat of Hulunbuir area and the water-fertilizer coupling mechanisms of cultivated land artificial grassland, so as to optimize the mode of planting management. 【Method】 The experiment was carried out at the Hulunber Grassland Ecosystem Observation and Research Station. On June 6, 2016, the experiment began with four blocks, each of which included three test factors pasture types (P) and nitrogen application level (N) and Irrigation (I); forage types included three treatments: alfalfa (P1), awnless brome (P2), and alfalfa and awnless brome 1:1 mixed sowing (P3); nitrogen application levels included no nitrogen (N0), low nitrogen (N1: 75 kgN·hm-2·a-1) and high nitrogen (N2: 150 kgN·hm-2·a-1). The hydration included two levels (I0: no water, I1: hydration). There were 72 test plots, each of which was 7 m×10 m, and the row spacing was 1 m; it replenished the water 3 times every year in June, July and August, and the water per unit area was 20 mm. The nitrogen application (chemical pure urea) was twice in the seedling (returning) and tillering stages, respectively. Grassland biomass, nutrients (plant crude protein, neutral detergent fiber and acid detergent fiber) and soil nutrients (soil total nitrogen, soil organic carbon and soil pH) were measured in 2016 and 2017. 【Result】 (1) The response of (N), (I), (P) and (P×I) to yield in the year of planting (2016) reached a significant level (P<0.05), and two measurements in 2017. The total yield of the production reached a significant level (P<0.05) in response to test factors such as (N), (P), (P×I), (P×N), (N×I×P), and mixed (P3). Under low water (I0) conditions, the yield of low nitrogen (N1) was significantly higher than that of the other treatment groups (P<0.05), with an average of 17 801.19 kg·hm-2. (2) The crude protein content in 2016 and 2017 were P1 treatment>P3 treatment>P2 treatment, in 2016. P1, P2 and P3 treatment showed that the CP content increased with the increase of nitrogen level when the hydration (I) conditions were the same, and P1 was not replenished under water (I0) conditions. The crude protein content under P1N2I0 was significantly higher than that under P1N0I0, P1N1I0, and P1N1I1 (P<0.05), reaching a maximum value of 19.08%; in 2017, under P3 at I0 conditions, the CP content of the lower N1 level (15.12%) was significantly higher than that of N0 (P<0.05). (3) Both nitrogen application and water addition promoted the negative growth of soil SOC content, positive TN content, and negative pH growth. The SOC growth of the topsoil and the bromegrass were significantly higher than that of the mixed seeding (P<0.05), and the TN growth of the topsoil was significantly higher than that of the bromegrass and mixed seeding (P<0.05); under the surface and subsurface of 2016, the ratio of soil carbon to nitrogen (C/N) was higher than that of 2017, the average surface layer was 17.39% higher, and the subsurface layer was 15.18% higher. The carbon and nitrogen ratio of surface soil was more obvious. The surface soil carbon and nitrogen ratio was P1N0I1 in 2016, with the highest value of 8.15; in 2017, the highest value under P1N2I0 was 5.67. The carbon and nitrogen in the subsurface soil was 6.36 higher than that under P1N2I1 in 2016, and the highest under P3N2I1 in 2017 was 5.67. 【Conclusion】 In the second year of planting in Hulunber, the coupling effect of herbage, water and nitrogen fertilizer had a significant effect on the biomass of the grass. The coupling effect of water and nitrogen fertilizer had a synergistic effect on the nutrient accumulation of the grass. The construction of artificial grassland plant could reduce a C/N and soil quality to drop, and adding in different kinds of grass, and water and nitrogen levels all showed the 0-20 cm soil SOC content and pH value were lower and soil TN content increased, indicating that soil acidification occurs, bean-grain mixed soil pH lower amplitude was less than unicast, and high nitrogen and filling water could be reduced to a significantly increased the soil pH value.

Key words: artificial grassland, nitrogen application, adding water, mixed sowing of bean-grass, community biomass, soil nutrients, Hulunber