九龙江流域大气氮湿沉降研究

通过2004～2005年对位于我国东南沿海的九龙江流域及周边共17个站点的实地观测,运用GIS技术定量揭示了大气氮湿沉降强度和时空分布特征,并利用氮稳定同位素分析雨水硝态氮的主要来源.结果表明,①17个站点雨水总氮平均浓度为(2.20±1.69)～(3.26±1.37) mg·L-1(以N计,下同),铵态氮、硝态氮和有机氮分别占39%、25%和36%;②雨水氮浓度随降雨强度的增大呈降低趋势,旱季浓度明显大于雨季,降水对大气具有清洗作用;③低δ15N值表明雨水硝态氮主要来源于汽车尾气排放、化石燃料燃烧和化肥施用;④九龙江流域大气氮湿沉降量平均9.9 kg·hm-2,春夏2季约占全年的91%,大气氮湿沉降占沉降总量的66%,揭示了该地区1∶2的大气氮干湿沉降结构.大气氮湿沉降时空差异与降雨量和氮的排放直接相关.

Wet Deposition of Atmospheric Nitrogen in Jiulong River Watershed

Spatio-temporal distributions and sources of atmospheric nitrogen (N) in precipitation were examined for Jiulong River Watershed (JRW), an agricultural-dominated watershed located in southeastern China with a drainage area of 1.47 x 10(4) km2. During 2004-2005, 847 rain samples were collected in seventeen sites and analyzed for ammonium N, nitrate N and dissolved total N (DTN) followed by filtration through 0.45 microm nucleopore membranes. Atmospheric N deposition flux was calculated using GIS interpolation technique (Universal Kriging method for precipitation, Inverse distance weighted technique for N) based on measured N value and precipitation data from eight weather stations located in the JRW. ArcView GIS 3.2 was used for surface analysis, interpolation and statistical work. It was found that mean DTN concentration in all sites ranged between 2.20 +/- 1.69 and 3.26 +/- 1.37 mg x L(-1). Ammonium, nitrate and dissolved organic N formed 39%, 25% and 36% of DTN, respectively. N concentration decreased with precipitation intensity as a result of dilution, and showed a significant difference between dry season and wet season. The low isotope value of nitrate delta 15N ranging between -7.48 per thousand and -0.27 per thousand (mean: -3.61 per thousand) indicated that the increasing agricultural and soil emissions together with fossil combustions contributed to atmospheric nitrate sources. The annual wet deposition of atmospheric N flux amounted to 9.9 kg x hm(-2), which accounts for 66% of total atmospheric N deposition flux (14.9 kg x hm(-2)). About 91% of wet atmospheric deposition occurred in spring and summer. The spatio-temporal variation of atmospheric N deposition indicated that intensive precipitation, higher ammonia volatilization from fertilizer application in the growing season, and livestock productions together provided the larger N source.