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山西省太原市旱作农区大气活性氮干湿沉降年度变化特征
引用本文:刘平,刘学军,刘恩科,韩彦龙,李丽君,白光洁,许稳,吕薇,张强.山西省太原市旱作农区大气活性氮干湿沉降年度变化特征[J].中国生态农业学报,2017,25(5):625-633.
作者姓名:刘平  刘学军  刘恩科  韩彦龙  李丽君  白光洁  许稳  吕薇  张强
作者单位:1. 山西省农业科学院农业环境与资源研究所/山西省土壤环境与养分资源重点实验室 太原 030031;2. 中国农业大学资源与环境学院 北京 100193;3. 山西省农业科学院旱地农业研究中心 太原 030031
基金项目:山西省财政支农项目(2016ZZCX-13)、山西省回国留学人员科研资助项目(2016-133)和2016年度人力资源和社会保障部留学人员科技活动项目择优资助
摘    要:鉴于大气氮素沉降对整个生态系统的重要影响,我国近年来陆续开展了不同尺度的大气氮素干、湿沉降的研究,但少有农业区多年连续监测的资料。本研究利用DELTA系统、被动采样器和雨量器在山西省太原市郊区阳曲县河村旱作农业区进行了4年的监测试验,观测大气氮素干、湿沉降的时间变异。结果表明:2011年4月—2015年3月,河村4年大气活性氮NH_3、HNO_3、NO_2、颗粒态NO_3~-(pNO_3~-)、颗粒态NH_4~+(pNH_4~+)平均沉降量分别为4.50 kg(N)·hm~(-2)·a~(-1)、3.54 kg(N)·hm~(-2)·a~(-1)、2.56 kg(N)·hm~(-2)·a~(-1)、1.62 kg(N)·hm~(-2)·a~(-1)、2.75 kg(N)·hm~(-2)·a~(-1),大气氮素干沉降总量为12.38~18.95 kg(N)·hm~(-2)·a~(-1),以2011年的氮干沉降量最高,2014年的最低。2011年4月—2015年3月各月氮干沉降量与氨气沉降量之间存在显著正相关,相关系数在0.809 8~0.937 1,由此可知,该地区活性氮沉降主要受农业氨气排放的影响。河村4年雨水中NO_3~-、NH_4~+平均浓度分别为3.20 mg(N)·L~(-1)和2.43 mg(N)·L~(-1),大气氮素湿沉降11.67~41.31 kg(N)·hm~(-2)·a~(-1)。年度间氮素湿沉降存在很大差异,以2012年氮素年湿沉降量最高,2014年最低,每年大气氮素湿沉降占氮总沉降量的份额超过50%。此外,4年湿沉降中不仅NO_3~--N和NH_4~+-N之间、且二者与降雨量也呈显著线性或二次相关关系,说明降雨量对NO_3~--N和NH_4~+-N的湿沉降影响较大。本研究表明太原市旱作农区不同年份间氮素湿沉降比干沉降差异更大,且总沉降数量较高。虽然是旱作区,该地区氮素干沉降略低于湿沉降。研究结果为该地区农田氮肥施用和氮素循环监测提供了理论依据。

关 键 词:活性氮  干沉降  湿沉降  年度变化  旱作农区
收稿时间:2016/11/16 0:00:00
修稿时间:2016/12/14 0:00:00

Temporal variation of atmospheric wet/dry reactive nitrogen deposition in Taiyuan rainfed farming area of Shanxi Province
LIU Ping,LIU Xuejun,LIU Enke,HAN Yanlong,LI Lijun,BAI Guangjie,XU Wen,LYU Wei and ZHANG Qiang.Temporal variation of atmospheric wet/dry reactive nitrogen deposition in Taiyuan rainfed farming area of Shanxi Province[J].Chinese Journal of Eco-Agriculture,2017,25(5):625-633.
Authors:LIU Ping  LIU Xuejun  LIU Enke  HAN Yanlong  LI Lijun  BAI Guangjie  XU Wen  LYU Wei and ZHANG Qiang
Institution:Institute of Agricultural Environment and Resources, Shanxi Academy of Agricultural Sciences/Shanxi Key Laboratory of Soil Environment and Nutrient Resources, Taiyuan 030031, China,College of Resources and Environmental Sciences, China Agricultural University, Beijing 100193, China,Institute of Dryland Farming, Shanxi Academy of Agricultural Sciences, Taiyuan 030031, China,Institute of Dryland Farming, Shanxi Academy of Agricultural Sciences, Taiyuan 030031, China,Institute of Agricultural Environment and Resources, Shanxi Academy of Agricultural Sciences/Shanxi Key Laboratory of Soil Environment and Nutrient Resources, Taiyuan 030031, China,Institute of Agricultural Environment and Resources, Shanxi Academy of Agricultural Sciences/Shanxi Key Laboratory of Soil Environment and Nutrient Resources, Taiyuan 030031, China,College of Resources and Environmental Sciences, China Agricultural University, Beijing 100193, China,Institute of Agricultural Environment and Resources, Shanxi Academy of Agricultural Sciences/Shanxi Key Laboratory of Soil Environment and Nutrient Resources, Taiyuan 030031, China and Institute of Agricultural Environment and Resources, Shanxi Academy of Agricultural Sciences/Shanxi Key Laboratory of Soil Environment and Nutrient Resources, Taiyuan 030031, China
Abstract:Nitrogen (N) deposition has a series of negative effects on ecosystem, therefore the atmospheric reactive N (Nr) pollution and deposition induced by excessive anthropogenic Nr have become a global environmental concern. Until recent years, researches on Nr deposition and precipitation were conducted at different scales, but still there are few continuous monitoring data about N deposition in rainfed farming areas. Here, the temporal variation of atmospheric wet and dry N deposition was quantified using the DELTA system, passive samplers and rain gauge at Hecun Village (which is Yangqu County, Taiyuan City, Shanxi Province) in a four-year period spanning from April 2011 to March 2015. The results showed the average deposition rates of NH3, HNO3, NO2, particle form of NO3- (pNO3-) and particle fore of NH4+ (pNH4+) in the four-year period were 4.50 kg(N)·hm-2·a-1, 3.54 kg(N)·hm-2·a-1, 2.56 kg(N)·hm-2·a-1, 1.62 kg(N)·hm-2·a-1 and 2.75 kg(N)·hm-2·a-1, respectively. This led to total dry deposition value of 12.38-18.95 kg(N)·hm-2·a-1, with N dry deposition flux being the highest in 2011, and the lowest in 2014. From April 2011 to March 2015, there was a positive linear correlation between monthly dry N deposition and ammonia deposition (with a correlation coefficient range of 0.809 8-0.937 1), indicating that ammonia had a significant influence on N deposition of the study area. Total wet N precipitation range was 11.67-41.31 kg(N)·hm-2·a-1 in the region and the average concentrations of NO3--N and NH4+-N in rainfall were 3.20 mg(N)·L-1 and 2.43 mg(N)·L-1, respectively. There were considerable differences in annual wet N deposition fluxes in the four-year period, of which it was the highest in 2012 and the lowest in 2014. Moreover, wet N deposition accounted for over 50% of total N deposition. Furthermore, there was a positive linear correlation between NO3--N and NH4+-N concentrations in rainwater in the four-year period, and there was also a positive linear correlation between NO3--N concentration and rainfall and then a quadratic correlation was also observed between NH4+-N concentration and rainfall. This indicated that rainfall had a significant impact on wet depositions of NO3--N and NH4+-N. Such high deposition rates of Nr in Taiyuan showed a severe Nr pollution from anthropogenic sources and a significant atmospheric N input in croplands. Overall, there were bigger differences in annual wet N deposition than annual dry N deposition for the investigated four-year period in Taiyuan area. Although tested in dry land, the rate of dry deposition was lower than that of wet precipitation. This study was important for N management referring to Nr deposition in farmlands and for monitoring N cycle in the farmland ecosystem.
Keywords:Reactive nitrogen  Dry deposition  Wet deposition  Annual variation  Rainfed farming area
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