大气氮沉降通量观测方法

工农业的发展引起含氮化合物排放量日益增多,导致大气向地面输入的沉降量相应增加。大气氮沉降是自然生态系统重要的氮素来源,沉降量的增加必然会对生态系统的生物地球化学循环产生干扰。针对大气氮沉降组成复杂、时空变异性大、观测的技术方法不统一、研究结果之间可比较性差等关键科学问题,本文从大气氮沉降来源和组成出发,综述了过去几十年来国内外大气氮素干湿沉降在观测方法和测试手段方面的重要进展,详细描述了传统雨量计收集法、降水降尘仪法、阴阳离子交换树脂法、降尘缸收集法和沉降速率法等干、湿沉降观测方法的原理,对比不同方法存在的优点与不足;简要对比了国内外大气干、湿沉降通量状况,提供了大气氮沉降区域分布格局方面的量化信息;初步阐明了大气氮沉降观测研究的理论基础和观测原理,为对比分析不同观测方法获得的观测结果提供定性参考,并为不同生态系统氮沉降研究选择合理的观测方法提供理论依据。     

山西北部农村区域大气活性氮沉降特征

利用DELTA系统、被动采样器和雨量器在山西省北部生态脆弱区朔州的一个监测点通过一整年的监测试验,研究了该地区农村区域大气氮素干湿沉降的月际变化。结果表明:2011年该地区大气氮素湿沉降为12.43kgN hm~(-2)a~(-1),远低于华北平原大气氮素混合沉降的平均值28.0kg N hm~(-2)a~(-1),降水中铵态氮、硝态氮和有机氮平均分别为1.24 mg N/L、1.27 mg N/L、1.26mg N/L。大气氮素湿沉降的年内分布不均,60%的沉降集中在降水较丰沛的4-10月份。试验区干沉降以氧化态氮(HNO_3NO_2和pNO_3~-)的沉降为主,氧化态氮的干沉降量是还原态氮(NH_3和pNH_4~+)的1.37倍,大气氮素干沉降总量为35.43 kg N hm~(-2)a~(-1)。总体来看,作为典型的干旱区,该地区氮的干沉降是湿沉降的3倍,氮素干湿沉降总量达到47.86kg N hm~(-2)a~(-1)。此外,硝态氮和铵态氮在雨水中呈线性相关,而在PM_(10)颗粒物中乘幂正相关;雨水中总碳和总氮呈线性正相关,而PM_(10)颗粒物中二者呈二次多项式关系。鉴于朔州地区古城镇较高的氮沉降数量,应该对该地区输入农田的氮素环境养分引起足够重视。     

大气有机氮沉降研究进展

大气氮素沉降是全球氮素生物地球化学循环的一个重要部分,包括干?湿沉降两种,以无机态和有机态形式发生沉降。长期以来由于受研究方法的限制,国际上对大气氮素沉降的研究多集中在无机态氮的沉降上,忽视了对有机态氮形式发生的沉降,因而造成了人们对大气氮素沉降总量的低估。在全面总结国内外文献的基础上,综述了大气有机态氮沉降的研究进展,具体包括大气有机氮的来源、种类?雨水有机氮的测定方法?有机氮沉降对大气氮沉降总量(氮沉降总量=无机氮沉降 有机氮沉降)的贡献,以及有机氮沉降可能的生态效应等。最后,指出了今后我国大气有机氮沉降研究需要加强的主要方面。     

长白山森林生态系统大气氮素湿沉降通量和组成的季节变化特征

2009—2010年期间,利用雨量计收集法在长白山森林生态系统定位站开展定位观测,分析降水中氮素浓度,研究了该区域大气氮素湿沉降通量和组成的季节变化特征。结果表明,各形态氮素月均浓度之间差别较大,具有明显的季节性;其降水中浓度主要受降水量和降水频次的影响。全年氮素湿沉降中TN、TIN和TON的沉降量分别为27.64 kg N hm-2a-1、11.05 kg N hm-2a-1和16.59 kg N hm-2a-1,TON为沉降主体,占60.02%;其大气氮沉降量主要由降水量和降水中氮素浓度共同决定。该地区氮湿沉降量已处于我国中等水平,考虑到氮素的干湿沉降比例,本区域的年氮沉降量已接近或超过本区域的营养氮沉降临界负荷,存在一定的环境风险。该地区生长季(5—10月)的氮沉降量(16.59 kg N hm-2a-1)占全年氮沉降量的比例达到73.20%。生长季的氮沉降对于促进植物生长直接生态意义重大,而非生长季的氮沉降对于大量补充次年植物生长初期所需养分的间接生态意义明显。     

华北平原大气氮素沉降的时空变异

利用量雨器和湿沉降自动收集仪在华北平原9个监测点通过2a的试验,研究了农田生态系统中大气氮素沉降的时空变异。结果表明:华北平原大气氮素混合沉降的平均值为28.0 kg/(hm2.a),降水中铵态氮和硝态氮量平均分别为3.76 mg/L和1.85 mg/L。不同地区比较,北京大气氮素沉降为32.5 kg/(hm2.a),明显高于山东和河北两省的23.6 kg/(hm2.a)。北京各监测点的大气氮素沉降也存在明显空间变异,东北旺、房山的氮素沉降水平较高,延庆、顺义的氮素沉降水平较低。大气氮素沉降的年内分布不均,60%的沉降集中在降水较丰沛的6~9月份。氮素的输入与降雨量呈乘幂型正相关(r2=0.67),在农田生态系统中以铵态氮的沉降为主,铵态氮的沉降量是硝态氮的2.0倍;城市生态系统中以硝态氮的沉降为主,铵态氮的沉降量是硝态氮的0.79倍。在东北旺试验点近两年的监测结果表明,在等量降雨量条件下湿沉降输入的氮素(18~20.6 kg/hm2)明显低于混合沉降(26.3 kg/hm2),湿沉降的氮素输入仅占后者的73%,而混合沉降中的超量部分主要来自铵态氮,表明干沉降尤其是降尘带入的铵态氮也是华北平原大气氮素沉降的重要来源。     

我国雷州半岛典型农田大气氮沉降

近一个半世纪以来,粮食和能源需求导致活性氮创造的急剧增加,从而导致各种活性氮的排放及其沉降的增加。氮沉降引起土壤酸化,水体富营养化,及敏感生态系统植物多样性的丧失等不良生态效应。因此定量不同生态系统氮沉降量对于确定该地区生态系统安全及氮循环有重要意义。南方地区氮沉降已有较多研究,主要集中于湿沉降的研究,选取雷州半岛地区典型农田综合研究了大气氮素的干湿沉降。结果表明:大气活性氮浓度NH3、HNO3、NO2、pNH+4和pNO-3浓度分别为5.62、0.88、3.16、3.30、2.02μg N/m3。采用欧洲氮沉降监测网的氮干沉降速率估算了大气氮干沉降量为17.6 kg N hm-2a-1。大气降雨NO-3-N浓度为(0.86±0.36)mg N/L,NH+4-N浓度为(1.11±0.68)mg N/L,大气降雨无机氮含量冬季最高,夏季最低。大气无机氮年湿沉降总量为25.3 kg N/hm2。湿沉降NH+4-N和NO-3-N,干沉降NH3、HNO3、NO2、pNH+4、pNO-3分别占沉降量的30.8%、28.0%、23.7%、5.4%、2.8%、3.9%、5.4%。湿沉降NH+4和干沉降NH3在氮沉降中占主导地位显示氮肥施用导致的NH3挥发对大气活性氮浓度及氮沉降的显著贡献。鉴于研究可观的氮沉降量(总沉降量42.9 kg N hm-2a-1),其向农田的养分的输入不容忽视;氮沉降对该地区水体,自然生态系统的环境影响需要受到重视。     

森林土壤氮素转换及其对氮沉降的响应

近几十年人类活动向大气中排放的含氮化合物激增 ,并引起大气氮沉降也成比例增加。目前 ,氮沉降的增加使一些森林生态系统结构和功能发生改变 ,甚至衰退。近 2 0 a欧洲和北美有关氮沉降及其对森林生态系统的影响方面的研究较多 ,而我国少有涉及。森林土壤氮素转换是森林生态系统氮素循环的一个重要的组成部分 ,而矿化、硝化和反硝化作用是其核心过程 ,氮沉降作为驱动因子势必改变森林土壤氮素转换速度、方向和通量。根据国外近 2 0 a有关研究 ,首先介绍了森林土壤氮素转换过程和强度 ,论述森林土壤氮素在生态系统氮素循环中的作用 ,然后在此基础上 ,介绍了氮沉降对森林土壤氮素循环的研究途径 ,探讨了氮沉降对森林土壤氮素矿化、硝化和反硝化作用的影响及其机理     

陕北典型农区大气干湿氮沉降季节变化

为了研究大气通过干湿沉降输入到农田土壤的氮通量,2007年6月至2008年5月在陕西榆林和洛川两地进行了为期一年的观测试验.结果表明:榆林和洛川地区大气总无机氮沉降通量分别为22.17和16.95 kg·hm~(-2)·a~(-1),湿沉降分别占95.1%和90.4%,干沉降分别占4.9%和9.6%,两个地区氮沉降均以湿沉降为主.总无机氮沉降中,NO_3~--N分别为12.22和9.24 kg·hm~(-2)·a~(-1),分别占总无机氮沉降量的55.1%和54.5%.由于污染水平、气象条件、下垫面特性等的差异,总无机氮沉降中,湿沉降量和NO_3~--N沉降量均是榆林地区大于洛川地区.     

离子树脂法测定森林穿透雨氮素湿沉降通量——以千烟洲人工针叶林为例

穿透雨是大气氮素输入森林生态系统的重要途径之一,穿透雨中氮素含量的定量评估在森林生态系统氮素循环研究中的作用不可忽视。穿透雨中氮沉降通量的空间异质性很强,传统降水收集法工作量大,且容易带来测定误差。分析了国产离子树脂测定大气氮素湿沉降的可行性,并以千烟洲人工针叶林为例探讨离子树脂法测定森林穿透雨的适用性。结果表明,离子交换树脂法和传统降水收集法测定值之间的相关性显著,离子交换树脂法可以很好的反映大气氮沉降通量和季节变化特征,并且在采样周期较长时也能准确测定氮沉降组分,是适用于野外站点林内穿透雨氮沉降通量的观测方法。千烟洲人工针叶林穿透雨的氮沉降通量为9.19 kgN?hm-2?a-1,夏季的5—7月份和冬季的1—2月份出现氮沉降通量高峰。夏季穿透雨氮沉降以铵态氮为主,而冬季以硝态氮为主。千烟洲人工针叶林的氮沉降通量与附近地区针叶林穿透雨氮沉降通量近似,低于临近区域阔叶林穿透雨的氮沉降通量水平,但已可能接近森林生态系统氮输出出现强烈反应的氮沉降临界值。     

鄂西北丹江口库区大气氮沉降

利用雨量器在鄂西北丹江口库区连续3a采集降雨样品,研究了大气氮沉降的变化动态。结果表明:2009—2011年月均总氮(TN)浓度为3.70—10.36 mg/L,与当月降雨量呈极显著线性负相关(R=-0.592**,n=32),季均TN浓度为冬季(8.21 mg/L)春季(3.94 mg/L)秋季(3.23 mg/L)夏季(2.70 mg/L),年均TN浓度为3.70 mg/L。大气氮素年均干湿总沉降量为26.53 kg/hm2,其中干沉降为7.80 kg/hm2,占总沉降量的29.4%;湿沉降为18.73 kg/hm2,占总沉降量的70.6%。干沉降中铵态氮(NH+4-N)、硝态氮(NO-3-N)、可溶性有机氮(DON)和颗粒态氮(PN)分别占TN的22.1%、16.8%、37.2%和23.9%,湿沉降中它们分别为TN的36.6%、34.4%、12.9%和16.1%。     

大气氮沉降监测方法研究进展

大气氮沉降是全球氮素生物地球化学循环中的重要环节,指包括氧化态(NO_y)和还原态(NH_x)的活性氮通过干、湿沉降两种方式从大气中移除并降落到地表的过程,对陆地和水生生态系统的结构和功能有重要影响.日益增加的氮沉降对自然生态系统和人类健康构成潜在威胁,如何准确监测不同生态系统的干、湿氮沉降的组成和通量,建立统一的监测技术方法是近年来的研究热点和难点之一.本文详细综述了近年来国内外干、湿氮沉降的监测方法,包括微气象学法、推算法、模型法、替代面法、降水采集法和离子交换树脂法等.并结合其在区域、国家及全球尺度的应用对比总结了不同方法的优缺点,为建立全国性的氮沉降监测网络提供方法学的支持.     

Roads as nitrogen deposition hot spots

Mobile sources are the single largest source of nitrogen emissions to the atmosphere in the US. It is likely that a portion of mobile-source emissions are deposited adjacent to roads and thus not measured by traditional monitoring networks, which were designed to measure long-term and regional trends in deposition well away from emission sources. To estimate the magnitude of near-source nitrogen deposition, we measured concentrations of both dissolved inorganic nitrogen (DIN) and total dissolved nitrogen (inorganic + organic) (TDN) in throughfall (i.e., the nitrogen that comes through the forest canopy) along transects perpendicular to two moderately trafficked roads on Cape Cod in Falmouth MA, coupled with measurements of both DIN and TDN in bulk precipitation made in adjacent open fields at the same transect distances. We used the TDN throughfall data to estimate total nitrogen deposition, including dry gaseous nitrogen deposition in addition to wet deposition and dry particle deposition. There was no difference in TDN in the bulk collectors along the transects at either site; however TDN in the throughfall collectors was always higher closest to the road and decreased with distance. These patterns were driven primarily by differences in the inorganic N and not the organic N. Annual throughfall deposition was 8.7 (±0.4) and 6.8 (±0.5) TDN kg N ha^?1 year^?1 at sites 10 and 150 m away from the road respectively. We also characterized throughfall away from a non-road edge (power line right-of-way) to test whether the increased deposition observed near road edges was due to deposition near emission sources or due to a physical, edge effect causing higher deposition. The increased deposition we observed near roads was due to increases in inorganic N especially NH₄ ⁺. This increased deposition was not the result of an edge effect; rather it is due to near source deposition of mobile source emissions. We scaled these results to the entire watershed and estimate that by not taking into account the effects of increased gaseous N deposition from mobile sources we are underestimating the amount of N deposition to the watershed by 13–25 %.     

Factors controlling soil development in sand dunes: evidence from a coastal dune soil chronosequence

Aerial photographs, maps and optically stimulated luminescence dates were combined with existing soil data to construct high resolution chronosequences of soil development over 140 years at a temperate Atlantic UK dune system. Since soil formation had progressed for varying duration under different climate and nitrogen deposition regimes, it was possible to infer their relative influence on soil development compared with location-specific variables such as soil pH, slope and distance to the sea. Results suggest that soil development followed a sigmoid curve. Soil development was faster in wet than in dry dune habitats. In dry dunes, rates were greater than in the literature: they increased with increasing temperature and nitrogen deposition and decreased with increasing summer gales. The combination explained 62% of the variation. Co-correlation meant that effects of nitrogen deposition could not be differentiated from temperature. In wet dune habitats rates increased with temperature and decreased with gales. The combination explained only 23% of the variation; surprisingly, rainfall was not significant. Effects of location-specific variables were not significant in either habitat type. Nitrogen accumulation was faster in wet than dry dune habitats, averaging 43 kg N ha^?1 per year overall. Nitrogen accumulation greatly exceeded inputs from atmospheric deposition, suggesting rates of input for biological N fixation are 10–60 kg N ha^?1 per year. Recent climate and/or nitrogen deposition regimes may have accelerated soil development compared with past rates. These data suggest the importance of changing climate on soil development rates and highlight the contribution of biological N fixation in early successional systems.     

亚热带典型流域C、N沉降季节变化特征及其耦合输出过程

大气湿沉降是流域生态系统水体中碳氮的重要来源,对生态系统的健康及稳定性有很大的影响。通过对江西千烟洲典型亚热带流域降雨过程的碳、氮湿沉降和径流过程的季节性动态特征进行监测分析,探讨流域沉降、径流输出的C、N耦合及平衡关系。结果表明:千烟洲香溪流域降雨径流中碳氮浓度明显低于雨水,流域大气降水中DOC浓度和TN浓度呈极显著正相关关系。香溪河流域常规水体C∶N均值为2.81,远低于根据Redfield比率得出的适宜浮游生物生长的C∶N(6.6左右),说明外源性N输入导致该流域水体环境处于N过量的状态,长期输出会提高下游鄱阳湖水系的营养化程度。降雨过程对流域碳输入输出平衡影响较小,对氮输入输出平衡的影响较大。流域湿沉降DOC年输入量为69.41 kg hm~(-2)a~(-1),TN湿沉降通量为77.23 kg hm~(-2)a~(-1),碳氮沉降水平受区域降雨量及空气污染情况控制。香溪流域生态系统截留的沉降TN占当地氮肥年均使用量的33.13%,大气降水对亚热带流域生态系统的大量营养物质输入不容忽视。     

Annual nitrogen budget of a temperate coastal barrier salt-marsh system along a productivity gradient at low and high marsh elevation

An annual nitrogen budget was established for a temperate back barrier salt-marsh system along a productivity gradient at low and high marsh elevation. We measured plant biomass and nitrogen content in three plant compartments to deduce plant N-allocation patterns. Measurements were done along a successional sequence in a salt-marsh system. In addition, N-mineralization, wet and dry atmospheric N-deposition and sediment N-deposition were measured.

Plant-species dominance changed along the successional sequence. In early stages, Elymus farctus and Spergularia media formed a large part of total plant biomass. Festuca rubra and Puccinellia maritima were dominant at intermediate stages, whereas Elymus pycnanthus and Limonium vulgare were dominant at late stages of succession. Shoot biomass was highest in June, whereas litter biomass was highest in September and December. Root biomass formed by far the largest fraction of total plant biomass, especially at a low-marsh elevation.

Wet deposition of nitrate and ammonium was 1.7 g N m⁻² yr⁻¹, whereas throughfall deposition (dry and wet deposition) amounted to 2.1–3.6 g N m⁻² yr⁻¹, and was positively related to the height of an artificial plant canopy. Sediment organic nitrogen deposition rate was 0.3–5.4 g N m⁻² yr⁻¹, and negatively related to marsh elevation. Nitrogen mineralization rate increased from 2.5–2.8 g N m⁻² yr⁻¹ in young marshes towards 8.0–12.7 g N m⁻² yr⁻¹ at older marshes, depending on marsh elevation.

At a low-marsh elevation, plant N-availability depended equally on tidal N, atmospheric N and mineralized N, especially in young marshes, whereas the decomposition pathway became more important in older marshes. Tidal N contributed most to ecoystem N-accumulation rate at early successional stages, whereas atmospheric N was more important at later stages. Tidal influence was low at high-marsh elevation sites. Here, atmospheric deposition was the dominant exogenous nitrogen source both in young and old marshes.     

Inertia in an ombrotrophic bog ecosystem in response to 9 years' realistic perturbation by wet deposition of nitrogen,separated by form

Wet deposition of nitrogen (N) occurs in oxidized (nitrate) and reduced (ammonium) forms. Whether one form drives vegetation change more than the other is widely debated, as field evidence has been lacking. We are manipulating N form in wet deposition to an ombrotrophic bog, Whim (Scottish Borders), and here report nine years of results. Ammonium and nitrate were provided in rainwater spray as NH₄Cl or NaNO₃ at 8, 24 or 56 kg N ha^?1 yr^?1, plus a rainwater only control, via an automated system coupled to site meteorology. Detrimental N effects were observed in sensitive nonvascular plant species, with higher cumulative N loads leading to more damage at lower annual doses. Cover responses to N addition, both in relation to form and dose, were species specific and mostly dependent on N dose. Some species were generally indifferent to N form and dose, while others were dose sensitive. Calluna vulgaris showed a preference for higher N doses as ammonium N and Hypnum jutlandicum for nitrate N. However, after 9 years, the magnitude of change from wet deposited N on overall species cover is small, indicating only a slow decline in key species. Nitrogen treatment effects on soil N availability were likewise small and rarely correlated with species cover. Ammonium caused most N accumulation and damage to sensitive species at lower N loads, but toxic effects also occurred with nitrate. However, because different species respond differently to N form, setting of ecosystem level critical loads by N form is challenging. We recommend implementing the lowest value of the critical load range where communities include sensitive nonvascular plants and where ammonium dominates wet deposition chemistry. In the context of parallel assessment at the same site, N treatments for wet deposition showed overall much smaller effects than corresponding inputs of dry deposition as ammonia.     

太湖地区氮素湿沉降动态及生态学意义：以常熟生态站为例

在常熟生态站2001年6月至2003年5月连续两年定位收集湿沉降,对太湖地区氮素湿沉降动态进行研究．结果表明,湿沉降氮输入量季节变化显著,夏、春季高,秋、冬季低．在湿沉降输入氮中NH4^+-N、NO3^--N和DON的比例分别为47．6％、35．1％和17．4％．湿沉降中NH4^+-N主要来自当地农田的氨挥发,湿沉降NH4^+-N月输入量随月降雨量增加而增加(R0=0．3178^**)．该地区空气中NO3^--N浓度相对比较稳定,湿沉降中NO3^--N浓度与降雨量呈负相关(R^2=0．4205^***)．湿沉降NO33^--N月输入量与月降雨次数呈直线正相关(R^2=0．6757***),而与月降雨量相关性较差(R^2=0．1985^*)．湿沉降TN年输入量为27．0kg·hm^-2,并在所有降雨中,氮浓度均超过水体富营养化阈值(0．2mg·L^-1)．     

丹江口水库淅川库区大气氮湿沉降特征

大气氮沉降是除河流输入外水库水体重要的外源氮输入途径。以丹江口水库淅川库区为研究区,于2018年11月至2019年10月在库区周边设置了6个采样点,采集并分析了库区大气氮湿沉降样品,探讨氮湿沉降的时空分布特征以及对水库水体外源氮输入的贡献。研究结果表明,研究区大气氮湿沉降量为24.21 kg hm^-2 a^-1,其中氨氮占比（47.45％）为最大,有机氮占比（36.34％）次之,硝氮占比（16.21％）最小。硝氮湿沉降量在空间上表现出显著差异性。氨氮、有机氮湿沉降量的季节差异显著,氨氮是以夏季最高,秋季次之,冬季最低,而有机氮是以秋季最高,夏季次之,冬季最低。氨氮、硝氮、有机氮湿沉降量之间存在显著相关性,氨氮、有机氮湿沉降量与降水量之间存在显著相关性。总氮、氨氮湿沉降量分别为1321.98 t/a和627.34 t/a,分别占河流总氮、氨氮入库量的10.82％、34.85％。研究结果可为探索有针对性的库区水体氮污染控制途径提供重要理论基础。