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1.
地下水硝酸盐氮同位素分析最新方法——细菌反硝化法   总被引:5,自引:2,他引:5  
细菌反硝化法是目前地下水中硝酸盐氮同位素分析的最新方法,包括反硝化菌的选取与培养、反硝化菌将硝酸盐完全转化成N2O气体、N2O气体的提取与纯化、N2O气体氮同位素测定。与传统方法相比,细菌反硝化法可分析低浓度微量水中硝酸盐氮同位素,且更为快捷可靠。  相似文献   

2.
海洋生态系统中的氮素生物地球化学循环主要是由微生物的代谢过程来驱动的,包括氮固定、氮同化、硝化以及反硝化和厌氧氨氧化过程,这些过程都伴随着不同程度的氮氧同位素的分馏,直接影响着海洋硝酸盐中的氮氧稳定同位素组成.因此,通过检测海洋硝酸盐中的氮氧稳定同位素信号,就可以捕捉到海洋中发生的具体氮素循环过程.细菌反硝化法是这一研究最有力的手段,通过细菌的作用把硝酸盐中记录的氮氧稳定同位素信号转化到N2O中,再通过痕量N2O的同位素质谱测定和分析,准确地反映海洋中发生的氮素转化过程.硝酸盐氮氧稳定同位素分馏过程为深入理解海洋氮循环提供了一个重要的工具,有力推动了海洋氮素生物地球化学的研究,在近10年来取得了重要进展.  相似文献   

3.
硝酸盐的氮和三氧同位素(δ15N, δ17O和δ18O)及氧同位素非质量分馏(△17O)综合研究, 可以更有效地示踪硝酸盐的来源和形成过程、制约硝酸盐的形成条件。本文详细描述了细菌反硝化法测定10–6级硝酸盐氮和三氧同位素的分析测试方法和实验要点。综合优化改良的细菌反硝化前处理方法、全自动气体预浓缩富集纯化系统和测试流程, 实现了实验室长期测定数据的稳定性, 以及多批次标准样品测定的良好重现性。10 nmol NO– 3标准样品的δ18O和δ15N测试精度分别是0.25‰(1σ)和0.40‰(1σ)。80 nmol NO– 3标准样品的δ18O、δ17O和δ15N的测试精度分别是0.5‰(1σ)、0.4‰(1σ)和0.1‰(1σ), 据此计算出的Δ17O精度为0.46‰(1σ)。  相似文献   

4.
硝酸盐氮氧同位素反硝化细菌法测试研究   总被引:2,自引:0,他引:2  
进入21世纪,硝酸盐氮氧同位素测试技术的显著进展是反硝化细菌法测试技术的建立。反硝化细菌法具有可同时分析浓度低至μg/L的硝酸盐氮氧同位素组成、免去复杂的样品预处理、分析时间大大缩短以及从复杂溶液中只转化NO3-为N2O等优点。实验过程由细菌挑选和培养、样品NO3-转化为N2O、N2O提取纯化、同位素测试以及同位素测试结果校正等几个关键步骤组成。国外研究结果显示该技术不仅可用于海水和淡水中硝酸盐同位素测试,而且还可用于土壤样品,并得到不断的完善和应用;国内建立了这一技术,在包气带和地下水硝酸盐污染研究中取得重要进展。由于该技术诸多优点,建议大力促进这一技术在我国的研究和应用,希望有关部门加大支持力度,进一步完善该技术并推广应用。  相似文献   

5.
氮、氧同位素在地下水硝酸盐污染研究中的应用   总被引:8,自引:0,他引:8  
周迅  姜月华 《地球学报》2007,28(4):389-395
硝酸盐是地下水中难以去除的稳定污染物之一,是地下水氮(N)污染的主要形式.不同氮来源的硝酸盐氮、氧(O)同位素组成不同,可利用N、O同位素并结合其他同位素技术示踪硝酸盐污染源,识别反硝化过程,对于有效控制污染源和评估地下水对硝酸盐污染的恢复自净能力有重要意义.本文介绍了N、O同位素技术在地下水硝酸盐污染源追踪和反硝化过程的识别方面的原理和应用以及目前发展状况.  相似文献   

6.
海水硝酸盐氮、氧同位素组成研究进展   总被引:2,自引:0,他引:2  
杨志  陈敏 《地球科学进展》2012,27(3):268-275
海洋中氮的生物地球化学循环影响着海洋生态系统的结构和功能,并和全球气候变化有着密切的联系,一直是海洋科学研究的重点和热点。海水硝酸盐的15N/14N和18O/16O比值可以反映海洋中氮循环的主要过程,因而成为研究海洋氮循环的一个重要手段。综述海水硝酸盐氮、氧同位素组成的测定方法,同化吸收作用、硝化作用、反硝化作用、生物固氮作用等氮循环过程所导致的氮、氧同位素分馏及其在海洋学研究中的应用。海洋生态系中硝酸盐氮、氧同位素的分布可以提供支持生物生产力的氮来源信息,以及氮在不同储库迁移转化的路径与机制。未来的研究需要发展适用于低含量硝酸盐的同位素测量方法,构筑海洋氮的收支平衡,掌握影响上层海洋硝酸盐氮、氧同位素变化的过程,获取全球海域有关硝酸盐氮、氧同位素组成的更多数据。  相似文献   

7.
针对硝酸盐对地下水污染的严重性,介绍了用CaO除去CO2和H2O的测定氮同位素比值的燃烧等方法和和利用AgNO3 C(石墨)生成CO2的测定NO^-3中氧同位素比值的燃烧法,研究了用^15N和^18O同位素分析地下水中NO^-3来源和判断硝化作用和反硝化作用的发生机理。  相似文献   

8.
地下水NO3-氮与氧同位素研究进展   总被引:1,自引:0,他引:1  
人为活动通常是地下水硝酸盐污染的主要原因.不同来源的NO3-具有不同的氮、氧同位素组成,利用地下水NO3-中的δ15N和δ18O值可有效识别地下水硝酸盐污染的来源.引起地下水中NO3-含量显著减少的不同物理、化学和生物过程,所产生的氮、氧同位素分馏效应有明显差别.地下水系统中反硝化作用发生时,NO3-中氮和氧同位素分馏系数呈一定比例.因此NO3-中δ15N和δ18O值也是示踪地下水硝酸盐循环,尤其是反硝化作用的有效手段.利用NO3-中氮和氧双同位素,并与其他环境同位素及化学分析技术相结合,示踪NO3-来源及其循环是地下水硝酸盐污染研究的重要方向之一.综述了利用地下水硝酸盐中氮和氧同位素识别NO3-污染源与循环的研究进展,简述了近年迅速发展的阴离子交换树脂取样法,概述了此方面研究存在的主要问题,并展望了今后的研究方向.  相似文献   

9.
氮氧同位素在河流硝酸盐研究中的应用   总被引:9,自引:0,他引:9  
多年来,世界各地河流普遍存在硝酸盐污染问题。为控制河流的硝酸盐污染,确定河水中硝酸盐的来源以及研究氮的循环过程就显得尤为重要。由于在不同成因下,硝酸盐的δ15N和δ18O存在着较大差异,因此利用氮、氧同位素方法研究河流硝酸盐问题正日益受到国内外研究人员的重视。综述了用硝酸盐中氮、氧同位素来研究河流硝酸盐的不同来源(大气沉降、化肥、牲畜粪、土壤硝酸盐等)和示踪其地球化学循环过程,特别是反硝化过程,这两方面的研究进展,并对我国河流硝酸盐研究现状进行了讨论及提出今后的研究方向。   相似文献   

10.
人为活动通常是地下水硝酸盐污染的主要原因。不同来源的NO3^-具有不同的氮、氧同位素组成,利用地下水NO3^-中的δ15N和δ18O值可有效识别地下水硝酸盐污染的来源。引起地下水中NO3^-含量显著减少的不同物理、化学和生物过程,所产生的氮、氧同位素分馏效应有明显差别。地下水系统中反硝化作用发生时,NO3^-中氮和氧同位素分馏系数呈一定比例。因此NO3^-中δ15N和δ18O值也是示踪地下水硝酸盐循环,尤其是反硝化作用的有效手段。利用NO3^-中氮和氧双同位素,并与其他环境同位素及化学分析技术相结合,示踪NO3^-来源及其循环是地下水硝酸盐污染研究的重要方向之一。综述了利用地下水硝酸盐中氮和氧同位素识别NO3^-污染源与循环的研究进展,简述了近年迅速发展的阴离子交换树脂取样法,概述了此方面研究存在的主要问题,并展望了今后的研究方向。  相似文献   

11.
The stable nitrogen isotopic composition of nitrate, concentrations of inorganic nitrogen and phosphorus, dissolved oxygen and nitrification rates were determined at six stations ranging from the oligotrophic North Pacific Subtropical Gyre (NPSG) to the more productive Eastern Tropical North Pacific (ETNP). Nitrification rates increased along the transect from a maximum rate of 1 nmol L−1 d−1 at station ALOHA to 23.7 nmol L−1 d−1 at station 6. In oxic surface waters, nitrate isotopically enriched in 15N (maximum δ15N-NO3 value of 12.5‰) was most likely the result of assimilatory nitrate reduction. In contrast, high δ15N-NO3 values (maximum of 12.3‰) in association with high nitrate deficits and anoxic conditions supported the interpretation of isotopic fractionation due to denitrification. A one-dimensional vertical advection and diffusion model was used to estimate the fractionation factor for denitrification at two stations in the ETNP. A comparison of modeled to observed δ15N-NO3 data indicated an isotopic enrichment factor (ε) of 30‰ at station 4 and 30 to 35‰ at station 5. Isotopically light nitrate (1.1 and 3.2‰) was observed in the upper 200 m of the water column at stations in the ETNP. Tracer studies of 15NH4 and biogeochemical indicators of nitrogen fixation supported the interpretation of nitrification as the most plausible explanation for low δ15N-NO3 values observed in water column samples. Our results are consistent with the occurrence of nitrification within the euphotic zone and for the first time provide corroborating stable nitrogen isotopic evidence for this process.  相似文献   

12.
The Nauset Marsh estuary is the most extensive (9.45 km2) and least disturbed salt marsh/estuarine system within the Cape Cod National Seashore, even though much of the 19 km2 watershed area of the estuary is developed for residential or commercial purposes. Because all of the Nauset watershed is serviced by on-site individual sewage disposal systems, there is concern over the potential impact of groundwater-derived nutrients passing from these systems to the shallow receiving waters of the estuary. The purpose of this study was to determine whether denitrification (the bacterial conversion of nitrate to gaseous nitrogen) in estuarine sediments could effectively remove the nitrate from contaminated groundwater before it passed from the watershed to the estuary. Rates of denitrification were measured both in situ and in sediment cores, in areas of active groundwater discharge, in relatively pristine locations, and in areas situated down-gradient of moderate to heavily developed regions of the watershed. Denitrification rates for 47 sediment cores taken over an annual cycle at 5 stations ranged from non-detectable to 47 μmol N2 m−2 h. Mean denitrification rates were positively correlated with sediment organic content, and varied seasonally due to changes in sediment organic content and to the effect of water temperatures on sediment oxygen penetration depths. There was no correlation between observed denitrification rates and corresponding nitrate concentrations in groundwater. A comparison of in situ denitrification rates (supported by groundwater nitrate) with denitrification rates observed in sediment cores (supported by remineralized nitrate) showed that groundwater-driven denitrification rates were small, and not in excess of denitrification rates supported by remineralized nitrate. Most of the denitrification in Nauset sediments was apparently fueled by remineralized nitrate through coupled nitrification/denitrification. Denitrification did not contribute significantly to the direct loss of nitrate from incoming groundwater at Nauset Marsh estuary. Groundwater flow was rapid, and much of it occurred in freshwater springs and seeps through very coarse, sandy, well-oxygenated sediments of limited organic content. There was little opportunity for denitrification to occur during groundwater passage through these sediments. These results have important management implications because they suggest that the majority of nitrogen from contaminated groundwater crosses the sediment/water interface and arrives at Nauset Estuary, where it is available to primary producers. Preliminary budget calculations suggest that while denitrification was not an effective mechanism for the direct removal of nitrate in contaminated groundwater flowing to Nauset Marsh estuary, it may contribute to significant nitrogen losses from the estuary itself.  相似文献   

13.
Nitrate pollution of groundwater in the Yellow River delta,China   总被引:8,自引:0,他引:8  
Nitrate pollution of groundwater in the Yellow River delta, China is an important issue related not only to nitrate dispersion and health concerns but also to mass transport and interactions of groundwater, sea, and river waters in the coastal area. The spatial distribution of nitrate, nitrate sources, and nitrogen transformation processes were investigated by field surveys and geochemical methods. Nitrate occurred mainly in shallow layers and had a spatial distribution coinciding with geomorphology and land/water use. Irrigation water from the Yellow River and anthropogenic waste are two main nitrogen sources of nitrate in the delta, and both denitrification and mixing processes could take place according to characteristics identified by ionic and isotopic data.  相似文献   

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