中国农业科学 ›› 2018, Vol. 51 ›› Issue (3): 523-534.doi: 10.3864/j.issn.0578-1752.2018.03.011

• 农牧系统养分管理 • 上一篇    下一篇

中国天然草地氮磷流动空间特征

魏志标1,2,柏兆海2,马林2,张福锁1   

  1. 1中国农业大学资源与环境学院/植物-土壤相互作用教育部重点实验室,北京 100193;2中国科学院遗传与发育生物学研究所农业资源研究中心/   河北省节水农业重点实验室/中国科学院农业水资源重点实验室,石家庄 050021
  • 收稿日期:2017-07-31 出版日期:2018-02-01 发布日期:2018-02-01
  • 通讯作者: 马林,E-mail:malin1979@sjziam.ac.cn
  • 作者简介:魏志标,E-mail:weizb1993@126.com
  • 基金资助:
    国家重点研发计划(2016YFD0800106,2016YFD0200105)、国家自然科学基金面上项目(31572210)、河北省杰出青年基金(D2017503023)、中国科学院百人计划项目

Spatial Characteristics of Nitrogen and Phosphorus Flow in Natural Grassland of China

WEI ZhiBiao1,2, BAI ZhaoHai2, MA Lin2, ZHANG FuSuo1   

  1. 1College of Resources and Environmental Sciences, China Agricultural University/Key Laboratory of Plant-Soil Interactions, Ministry of Education, Beijing 100193; 2Center for Agricultural Resources Research, Institute of Genetics and Developmental Biology, Chinese Academy of Sciences/Hebei Key Laboratory of Water-Saving Agriculture/Key Laboratory of Agricultural Water Resources, Chinese Academy of Sciences , Shijiazhuang 050021
  • Received:2017-07-31 Online:2018-02-01 Published:2018-02-01

摘要: 【目的】定量研究天然草地的氮磷流动空间特征,为优化牧草施肥和提高牧草产量提供科学依据。【方法】建立中国天然草地氮磷养分输入(输出)数据库,利用NUFER模型定量中国天然草地氮磷平衡账户、利用率和环境排放特征。【结果】(1)2013年,全国天然草地氮和磷的输入(输出)总量分别为5 034 Gg N和318 Gg P,单位面积的输入(输出)量分别为19 kg N·hm-21.2 kg P·hm-2。氮沉降和畜禽粪尿磷分别占氮和磷输入总量的49%和89%。各区域天然草地氮和磷输入(输出)量变化范围分别为7.0—70 kg N·hm-20.12—8.0 kg P·hm-2(2)2013年,天然草地氮和磷养分利用率分别为105%和191%,各区域间差异很大。中国各地区天然草地的氮利用率变化范围为67%—141%,磷利用率的变化范围为75%—538%;(3)2013年,天然草地氮和磷的环境损失量分别为1.7 kg N·hm-20.059 kg P·hm-2,氨挥发和侵蚀分别是氮和磷的主要损失途径。西南和东北地区天然草地氮损失量较多,部分区域的损失量超过8.0 kg N·hm-2;西北地区氮损失量较少,平均不足3.0 kg N·hm-2;青藏高原区氮损失量最少,不足1.0 kg N·hm-2。磷的环境排放空间规律与氮排放相似;(4)2013年,全国天然草地土壤氮和磷的亏缺总量分别为706 Gg N和315 Gg P,单位面积亏缺量分别为2.7 kg N·hm-21.2 kg P·hm-2。北方和西南部分地区天然草地的氮土壤累积量为负值,重庆、吉林和辽宁的土壤氮亏损量超过20 kg N·hm-2;西部和西南部分省份天然草地的氮土壤累积量为正值,其中广西和云南的土壤氮累积量超过5.0 kg N·hm-2。除广西和贵州外,其他区域天然草地磷养分均有不同程度的亏缺,重庆天然草地磷的亏缺量最大,为3.7 kg P·hm-2【结论】2013年,全国天然草地的氮和磷输入量较小,约50%的氮素通过氮沉降输入系统,约90%的磷素通过畜禽粪尿磷输入系统;全国天然草地土壤的氮和磷呈亏缺状态,养分利用率高于100%,当前草地系统不可持续,应注意补施氮磷养分;全国天然草地单位面积氮和磷的环境损失量较小,西南地区天然草地的氮和磷环境损失量大于其他区域。各区域天然草地氮磷流动空间特征差异较大。

关键词: 天然草地, 氮, 磷, 养分流动, 养分利用率, 土壤养分累积

Abstract: 【Objective】The objective of this study is to quantify the spatial characteristics of nitrogen (N) and phosphorus (P) flow in natural grassland of China, and to provide a scientific basis for optimizing forage fertilization and increasing forage yield. 【Method】The input and output database of N and P in natural grassland of China was established, the nutrient balance budget, nutrient use efficiency and environmental emission characteristics in natural grassland of China were quantified by using NUFER model. 【Result】(1) In 2013, the total input of N and P in natural grassland of China was 5 034 Gg N and 318 Gg P, respectively. The N and P input per unit area in natural grassland was 19 kg N·hm-2 and 1.2 kg P·hm-2, respectively. The N deposition and the manure P applied accounted for 49% and 89% of total N and P input. The range of input (output) of N and P in natural grassland in different regions was 7.0-70 kg N·hm-2 and 0.12-8.0 kg P·hm-2; (2) In 2013, the use efficiency of N and P in natural grassland of China was 105% and 191%, respectively. There were great differences among different regions. The range of use efficiency of N and P was 67%-141%, 75%-538%, respectively; (3) In 2013, the environmental loss of N and P in natural grassland of China was 1.7 kg N·hm-2 and 0.059 kg P·hm-2, respectively. Ammonia emission and erosion were the main loss pathways of N and P in natural grassland, respectively. The N loss in natural grassland of Southwest and Northeast China was over 8.0 kg·hm-2. The N loss of Northwest China was relatively low, which was less than 3.0 kg·hm-2 on average. The N loss in Tibet plateau was the lowest, which was less than 1.0 kg·hm-2. Spatial regularity of environmental P emission was similar to that of N emission; (4) In 2013, the total N and P deficit in natural grassland of China was 706 Gg N and 315 Gg P, respectively. The deficit per unit area of N and P was 2.7 kg N·hm-2 and 1.2 kg P·hm-2, respectively. The value of soil N accumulation in North and Southwest China was negative, and the soil N deficit in Chongqing, Jilin and Liaoning was more than 20 kg N·hm-2. The value of soil nitrogen accumulation in West and Southwest China was positive, and the soil N accumulation in Guangxi and Yunnan was more than 5.0 kg N·hm-2. Soil P accumulation in natural grassland of China was different from N accumulation. With the exception of Guangxi and Guizhou, all of other regions had a negative soil P accumulation. The P deficit of natural grassland in Chongqing was the largest, which was -3.7 kg P·hm-2. 【Conclusion】In 2013, the total input of N and P in natural grassland of China was relatively low, about 50% of the N was input through the N deposition and 90% of the P was input by manure P applied. The soil accumulation of N and P in natural grassland of China was negative in 2013, and the N and P use efficiency was higher than 100%. The current grassland system was unsustainable and applying moderate chemical fertilizers was sensible. In 2013, the environmental loss of N and P in natural grassland of China was relatively low. The nutrient loss in Southwest China was larger than that in other regions. The spatial flow characteristics of N and P in natural grassland varied greatly among different regions.

Key words: natural grassland, nitrogen, phosphorus, nutrient flow, nutrient use efficiency, soil nutrient accumulation