收稿日期: 2003-06-12
修回日期: 2003-08-18
网络出版日期: 2004-04-01
基金资助
国家自然科学基金项目“应用同位素技术改善石家庄地下水资源管理”(编号:40072083);国土资源部科技专项计划项目下属课题“人类活动对区域地下水循环演化的影响”(编号: 200010301-05)资助.
USING NITROGEN ISOTOPE TECHNIQUES TO IDENTIFY THE SOURCES OF THE NITRATE CONTAMINATION TO THE GROUNDWATER BENEATH SHIJIAZHUANG CITY
Received date: 2003-06-12
Revised date: 2003-08-18
Online published: 2004-04-01
地下水NO- 3污染是石家庄市地下水管理面临的一个主要问题。本次研究通过地下水及其潜在补给源的氮同位素和水化学调查,确定和识别石家庄市地下水NO- 3污染程度和污染源。地下水中的无机氮化合物主要以NO- 3形式存在,浓度变化在 2.65~152.1 m g/L之间,均值为(54.88± 31)m g/L( n=44),48%的样品浓度超过国际饮水标准(50 m g/L)。地下水样品的NO- 3- 15 N值域+4.53‰~+25.36‰,均值+9.94‰±4.40‰( n=34)。34个样品中,22个样品(65%)的氮同位素值大于+8‰;与1991年相比,氮同位素组成指示地下水NO- 3的主要来源已由当时矿化的土壤有机氮变为现在的动物粪便或污水;结合Cl-分析,南部地下水NO-3还受到东明渠污水的影响。其余12个样品(35%)的氮同位素值变化在+4‰~+8‰之间,其中 15 N值较大的(+6‰~+8‰)指示来自土壤有机氮,较小的(+4‰~+6‰)指示来自氨挥发较弱、快速入渗的化肥厂污水。根据上述研究结果,提出了改善石家庄市地下水管理的措施。
李政红 , 张翠云 , 刘少玉 , 张胜 . 利用氮同位素技术识别石家庄市地下水硝酸盐污染源[J]. 地球科学进展, 2004 , 19(2) : 183 -191 . DOI: 10.11867/j.issn.1001-8166.2004.02.0183
NO3-contamination in groundwater is one of the major problems confronted by groundwater management for Shijiazhuang City. In this study, nitrogen isotopes and hydrochemistry for groundwater and various potential recharge sources were investigated to determine and identify the extent and sources of contamination from NO3-in the groundwater beneath Shijiazhuang City. Inorganic nitrogen compounds in the groundwater mainly existed in the species of NO3-,whose concentrations ranged from 2.65 to 152.1 mg/L with a mean of 54.88±31mg/L([WTBX]n[WT]=44). Some 48% of the total samples had NO3- concentrations, which exceeded the drinking water standard of 50 mg/L. The 15N values of groundwater ranged from +4.53‰ to +25.36‰ with a mean of +9.94‰±4.40‰([WTBX]n[WT]=34). Of the 34 samples analyzed, 22 samples (65%) had greater 15N than +8‰. Compared with that in 1991, nitrogen isotopic compositions indicated that the major sources of NO3- in groundwater changed from mineralized soil organic nitrogen at that time to animal wastes or sewage at present. From the analysis of Cl-, NO3- in the groundwater in the southern part was also affected by sewage from Dongmingqu channel. The remaining 12 samples had a nitrogen isotopic signature of +4‰~+8‰, of which heavier end (+6‰~+8‰) suggested that NO3- mainly come from soil organic nitrogen mineralized and lighter end (+4‰~+6‰) was indicative of NO3-from effluents, which had weak ammonia volatilization and rapid filtration, discharged by fertilizer plants. Based on these studies, the measurements of groundwater management were recommended.
[1] Gilli G, Corrao G, Favilli S. Concentrations of nitrate in drinking water and incidence of gastric carcinomas: First descriptive study of the Piemonte region, Italy[J]. The Science of Total Environment, 1984, 34:35-48.
[2] Rademach J J, Young T B, Kanarek M S. Gastric cancer mortality and nitrate levels in Wisconsinn drinking water[J]. Archives of Environmental Health,1992, 47:292-294.
[3] Heaton T H E. Isotopic studies of nitrogen pollution in the hydrosphere and atmosphere: A review[J]. Chemical Geology, 1986, 59:87-102.
[4] Wassenaar L. Evaluation of the origin and fate of nitrate in the Abbotsford aquifer using the isotopes of 15N and18O in NO3 -[J]. Applied Geochemistry, 1995, 10: 391-405.
[5] Battaglin W A, Kendall C, Goolsby D A, et al. Plan of study to determine if the isotopic ratios 15N and δ18O can reveal the sources of nitrate discharged by the Mississippi river into the Gulf of Mexico(US Geological Survey Openfile Report 97-230)[EB/OL]. http://wwwrcolka.cr.usgs.gov/midconherb/isoprop.final.html.
[6] Kreitler C W. Determining the Source of Nitrate in Ground Water by Nitrogen Isotope Studies[R]. Report of investigations No.83. Bureau of Economic Geology, the University of Texas at Austin, Austin, Texas 78712. 1975.1-57.
[7] Kreitler C W. Nitrogen-isotope ratio studies of soils and groundwater nitrate from alluvial fan aquifers in Texas[J]. Journal of Hydrology, 1979,42:147-170.
[8] Gormly J R, Spalding R F. Sources and concentrations of nitratenitrogen in ground water of the Central Platte Region, Nebraska[J]. Ground Water, 1979, 3: 291-301.
[9] Komor S C, Henry W, Anderson Jr. Nitrogen isotopes as indicators of nitrate sources in Minnesota SandPlain aquifers[J]. Ground Water, 1993,31(2):260-270.
[10] Rivers C N,Barrett M H,Hiscock K M,et al. Use of nitrogen isotopes to identify nitrogen contamination of the Sherwood sandstone aquifer beneath the city of Nottingham, United Kingdom[J]. Hydrogeology Journal, 1996, 4(1):90-102.
[11] Shao Yisheng(邵益生), Ji Shan(纪杉). Applications of the nitrogen isotope method to studying impacts of irrigation with sewage on groundwater with nitrogen pollution[J]. Geotechnical Investigation & Surveying(工程勘察),1992, (4): 37-41(in Chinese).
[12] Jiao Pengcheng(焦鹏程),Yang Sugeng(杨素更), Wang Dongsheng(王东升), et al. Studies on Nitrogen Isotope Constitutes of Groundwater and Their Applications[R]. Project report supported by Geology Foundation, Contract No. 89018, Institue of Hydrogeology and Engineering Geology, Ministry of Geology and Mineral, 1992(in Chinese).
[13] Jiao Pengcheng(焦鹏程). 15N/14N ratios of ground water nitrate in Shijiazhuang City[J]. Bulletin of Chinese Academy of Geological Sciences(地球学报——中国地质科学院院报),1996,17(Supp):181-188(in Chinese).
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