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Nitrogen compounds emission and deposition inWest African ecosystems: comparison between wet and dry savanna

机译:西非生态系统中氮化合物的排放和沉积:湿大草原和干大草原之间的比较

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Surface emission and deposition fluxes of reactivenitrogen compounds have been studied in five sites ofWest Africa during the period 2002 to 2007. Measurementsof N deposition fluxes have been performed in IDAF sitesrepresentative of main west and central African ecosystems,i.e., _3 stations in dry savanna ecosystems (from 15° N to1_2° N), and _2 stations in wet savanna ecosystems (from 9° Nto 6° N). Dry deposition fluxes are calculated from surfacemeasurements of NO_2, HNO_3 and NH_3 concentrations andsimulated deposition velocities, and wet deposition fluxes arecalculated from NH+4 and NO~-_3 concentration in samples ofrain. Emission fluxes are evaluated including simulated NObiogenic emission from soils, emissions of NOx and NH_3from biomass burning and domestic fires, and volatilizationof NH_3 from animal excreta. This paper is a tentative to understandthe eventual impact of the monsoon variability fromyear to year, with the natural variability of local sources, onthe emission and deposition N fluxes, and to compare theseevolutions between dry and wet savanna ecosystems. In drysavanna ecosystems where the rain season lasts mainly fromJune to September, the occurence of rain correlates with thebeginning of emission and deposition fluxes. This link is lessobvious in wet savanna ecosystems (wet season mainly fromMay to October), where the surface is less submitted to drasticchanges in terms of water content. Whatever the location,the natural variability of rain from year to year does notexceed 15 %, and the variability of emission and depositionmagnitude ranges between 15% and _28 %. While quasi providingthe same total N budget, and due to the presence ofdifferent types of soils and vegetation, wet and dry savannado not present the same distribution in emission and depositionfluxes contributions: in dry savanna, the emission isdominated by ammonia volatilization, and the deposition isdominated by the dry contribution. In wet savanna, emissionis equally distributed between ammonia volatilization, emissionsfrom biomass burning and natural NO emissions fromsoils, and wet and dry deposition are equivalent. Due to thescarcity of available data on the African continent, and despitethe numerous uncertainties resulting from the differentcalculations and assumptions, this work is a combination ofdata from different origins (surface measurements, satelliteand modelling) to document the atmospheric Nitrogen cyclein tropical regions.
机译:在2002年至2007年期间,已在西非的五个地点研究了活性氮化合物的表面排放和沉积通量。在代表非洲西部和中部主要生态系统的IDAF地点(即干旱大草原生态系统中的_3站)进行了氮沉积通量的测量(从15°N到1_2°N),在湿大草原生态系统中有_2个站(从9°N到6°N)。通过NO_2,HNO_3和NH_3浓度的表面测量以及模拟的沉积速度来计算干沉降通量,并通过雨水样品中的NH + 4和NO〜-_3浓度来计算湿沉降通量。评估了排放通量,包括模拟的土壤中的非生物源排放,生物量燃烧和家庭火灾中的NOx和NH_3排放以及动物排泄物中的NH_3挥发。本文试图了解逐年季风变率的最终影响,以及当地来源的自然变率,对氮素通量的排放和沉积,并比较干旱和热带稀树草原生态系统的通量。在干旱季节主要从六月到九月的干旱草原生态系统中,降雨的发生与排放和沉积通量的开始有关。在湿的热带稀树草原生态系统(主要是从五月到十月的湿季)中,这种联系不太明显,在该生态系统中,地表水分含量变化不大。无论在何处,每年的降雨自然变化都不会超过15%,并且排放量和沉积量的变化范围在15%至_28%之间。虽然准总氮预算相同,并且由于存在不同类型的土壤和植被,湿和干热带稀树草原在排放量和沉积通量中的分布也不相同:在干燥热带稀树草原中,排放量以氨挥发为主,而沉积物为主由干贡献。在湿稀树草原中,排放物在氨气挥发,生物质燃烧产生的排放物和土壤中的自然NO排放物以及湿沉降和干沉降之间均等分布。由于非洲大陆可用数据的稀缺性,尽管计算和假设不同,不确定性也很多,但这项工作还是结合了来自不同来源(地表测量,卫星和模拟)的数据来记录热带地区的大气氮循环。

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