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本文使用中国科学院常熟和鹰潭生态实验站和气象站的观测资料，应用区域酸沉降模式系统（RegADMS）和大叶阻力相似模型来研究华东地区不同下垫面条件上的大气硫沉降问题，定量估计了农田下垫面上大气硫化物的沉降通量。SO2和硫酸盐的干沉降速率使用大叶阻力相似模型来估计，使用与降水量有关的参数化方案来确定湿沉降系数。结果表明，常熟地区农田下垫面的大气硫沉降通量为19．0gm^-2 a^-1，其中干沉降占42％；而位于江西红壤地区的鹰潭站的大气硫沉降通量为10．4gm^-2a^-1，其中干沉降占83％。比较发现，两地硫干沉降通量绝对值相差不大，但其在总沉降通量中所占的份额有较大差异；常熟站的硫湿沉降通量比鹰潭站要大9．23gm^-2a^-1，该差异是由两地污染状况和气象条件的不同造成。华东地区的年硫沉降总量为1．88Mt（1Mt=10^6t），其中72．8％沉降在农田下垫面上。硫沉降中43％是干沉降，57％是湿沉降。 相似文献
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典型大气污染物在不同下垫面上干沉积速率的动态变化及空间分布 总被引：17，自引：0，他引：17
利用中国科学院红壤生态试验站微气象站实测的梯度资料和大叶阻力相似沉积模型,计算了农田和森林下垫面大气污染物的干沉积速率,并将此模型嵌套到区域酸性沉降模式系统(RegADMS)中,模拟获得中国地区11种大气污染物干沉积速率的空间分布.结果表明:大气污染物干沉降速率(Vd)有明显的时间变化,物种的干沉积速率一般白天大于晚上,冬春季大于夏秋季节.大气污染物Vd也有明显的空间变化,中国地区SO2、HNO3、NO、NO2、NH3、O3、H2O2、TSP、PM10、SO2-4和NO-3年平均Vd分别为0.35士0.004、1.77±0.01、6.5 ×10-5±2.0×10-7、0.07±0.0007、0.28土0.003、0.20±0.001、0.54±0.002、7.2±0.0005、0.44±0.0005、0.25±0.0005、0.27±0.0008cm s-1.各种下垫面上粒子Vd差别不大,气体污染物在各下垫面上的Vd有所不同,表现为HNO3、NO2、O3的Vd在森林和草原上较大,而SO2、NH3、H2O2的Vd在水面上较大,NO的Vd都很小,且在各种下垫面上差别不大. 相似文献
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1998年 11月～ 1999年 10月间在中国科学院红壤站 (江西鹰潭 )农田小气候站进行了大气二氧化硫 (SO2 )、硫酸盐粒子 (SO2 -4)浓度采样和雨水样本收集 ,利用阻力模式和全年逐时气象资料计算 SO2 和 SO2 -4的干沉降速度 ,估算干沉降通量 ,利用降水资料和雨水中硫酸根离子浓度估计大气硫的湿沉降 ,从而定量研究大气硫沉降输入农田生态系统的通量 ,结果表明 :农田下垫面上 SO2 和 SO2 -4干沉降速度的年平均值分别是 0 .373± 0 .170 cm· s-1(月均值 0 .16 1～ 0 .5 45 cm·s-1)、0 .198± 0 .12 3cm· s-1(月均值 0 .15 2～ 0 .2 6 9cm· s-1)。农田下垫面硫年总沉降量为 10 .3g· m-2 ,其中干沉降占总沉降的 83.3%。硫的干沉降又以 SO2 的干沉降为主 ,占年干沉降总量的 92 .2 %。大气硫沉降输入占农田生态系统输入总量的 90 %以上 ,是农田生态系统获取硫素的一个重要途径 相似文献
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秋季在北京城郊草地下垫面上的一次臭氧干沉降观测试验 总被引：3，自引：0，他引：3
2007年9月23日至10月13日, 在北京昌平区蟒山森林公园内, 利用浓度梯度观测法研究了秋季草地下垫面上臭氧的干沉降特征。研究结果表明: (1) 整个观测期间, 臭氧干沉降通量和干沉降速率平均值分别为-0.40 μg?m-2?s-1(负号表示方向指向地面) 和0.55 cm/s。 (2) 臭氧干沉降通量和干沉降速率受观测点山谷风的影响, 当白天谷风主导时, 臭氧的干沉降通量最大, 其平均值为－0.67 μg?m-2?s-1; 在山风、 谷风转换期间, 其平均值为－0.44 μg?m-2?s-1; 夜间山风主导时最小, 为－0.26 μg?m-2?s-1。臭氧干沉降速率也呈现同样的变化规律, 三种情形下的平均沉降速率分别为0.74 cm/s、 0.50 cm/s和0.47 cm/s。 (3) 利用阻力模型计算了臭氧的植被冠层阻力 (Rc), 结果表明: 由于白天植被的光合作用, 叶面气孔打开, 冠层阻力相对较小, Rc 的平均值为109.0 s/m; 夜间植被叶面气孔关闭, 阻力有明显升高, Rc的平均值为217.7 s/m; 在整个观测期间, Rc的平均值为184.0 s/m。 相似文献
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影响气体和粒子干沉积的敏感因子分析 总被引：1，自引：0，他引：1
建立了一个模拟气体和气溶胶粒子在各种不同条件下干沉积的数学模式，用以研究了影响气体和粒子干沉积的敏感因子，从而进一步揭示物质干沉积和特征和规律，结果表明：下垫面的性质，气体本身与沉积表面的溶混性和表面的潮温程度是影响气体干沉积的重要因子；对粒子干沉积起主导作用的有粒子直径，平均风速、大气稳定状况和沉积表面的粗糙度。 相似文献
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北京奥运会前后静稳天气条件下SO2和NO2干沉降模拟 总被引：1，自引：0，他引：1
利用中国科学院大气物理研究所北京325m气象塔气象要素和污染物浓度观测资料,采用气体干沉降阻力模型,对奥运会前后北京行政区内SO2和NO2的干沉降影响因子、干沉降速率、干沉降通量进行数值模拟。结果表明:1)随着大气稳定度、太阳辐射强度和下垫面类型的改变,北京SO2和NO2的干沉降速率有明显变化,表面阻力是影响气体干沉降速率变化的主要因子。2)SO2和NO2在白天的干沉降速率及通量普遍大于夜晚。3)静稳天气条件下,奥运会前北京地区一天可清除24tSO2和55.2tNO2,奥运会期间一天可清除10.8tSO2和50.4tNO2,这说明北京及周边地区的减排措施对改善奥运会期间的空气质量效果显著。 相似文献
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利用次网格技术模拟华东地区大气硫氮沉降 总被引：5，自引：1，他引：5
采用数值模拟方法,在区域酸性沉降模式系统中引入次网格处理技术。通过4种次网格方案模拟结果的相互比较,选择最优方案,然后利用最优次网格方案,选取华东地区为例,进一步模拟研究大气硫氮沉降的空间分布。结果表明,就干沉积速率而言,以细网格方案(水平分辨率25 km)为参照,采用次网格方案比粗网格方案(水平分辨率75 km)有明显改进,其中“次网格风速与摩擦速度之积为常数”为最优次网格方案。华东地区硫的年总沉降量是1.92 mt(1 mt=106ton),氮的年总沉降量是0.65mt。华东地区硫化物(SO2、硫酸盐SO42-)干沉降量占总沉降量的49%,氮化物(NO、NO2、硝酸盐NO3-)干沉降量占总沉降量的80%,可见干沉降在大气沉降中具有重要地位。华东地区总的大气硫、氮沉降量中,70%以上到达有植被覆盖的土壤生态系统,这将对农田、草地和森林的硫素和氮素平衡有重要影响。此外,华东部分地区的硫沉降已经超过了临界负荷,而氮沉降尚未出现超临界负荷的现象。 相似文献
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半干旱地区地气界面水汽和二氧化碳通量的日变化及季节变化 总被引：19，自引：5，他引：19
采用涡动相关方法连续观测2002年10月到2003年12月半干旱地区地气界面水汽和二氧化碳通量变化,分析水汽和二氧化碳通量的季节和日变化规律,同时比较农田和退化草地两种不同下垫面物质和能量通量交换过程的差异,得到如下一些主要结果:(1)半干旱地区湿季,相距5 km的两种不同下垫面,即使在同一天气过程控制下,不同植被下垫面的降雨分布仍不尽相同,甚至相差很大.这表明降雨空间的分布是很不均匀的,具有很强的局地特征.(2)在干季近地面层能量收支中,两种不同下垫面上的有效能量(净辐射与地表热流量之差)主要分配为感热通量,潜热通量在非生长季(干季)通常很小.在湿季(生长季),潜热通量与感热通量相当,但农田下垫面的潜热通量大于退化草原下垫面.(3)土壤的温度和湿度日变化主要集中在0～20 cm土壤层内,在湿季农田下垫面土壤的湿度有明显的跳跃,这与降雨过程有很好的相关.(4)在非生长季,两种不同下垫面地气间二氧化碳通量差别不大,都很小.白天由于光合作用,在生长季农田下垫面吸收CO2通量较退化草原大,但比湿润地区稻田下垫面小一个量级,远小于森林生态系统. 相似文献
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利用大涡模式模拟了对流边界层结构演变以及深对流触发过程。通过改变鲍恩比的敏感性试验研究不同大气初始状况下湿润和干旱下垫面湍流特征及其对深对流触发过程的影响。结果表明:干旱下垫面的混合层干而暖,厚度较大;湿润下垫面相反。由于地表感热通量对热力湍流形成的作用更大,干旱下垫面上湍流混合和夹卷作用更强,使得水汽和相当位温在边界层内分布更均一,而在边界层顶有较大的负扰动;干旱下垫面上对流强度较湿润下垫面大,但均表现为泡状对流,水平方向上呈网状结构。不同下垫面上深对流的发生与大气初始状况有关,当初始时刻1—3 km的逆温强度较弱时（0.15 K/（100 m））,边界层内湍流迅速发展,深对流首先在干旱下垫面发生,但因对流有效位能较小,云层厚度小于湿润下垫面。当1—3 km的逆温强度增加到0.55 K/（100 m）时,云层形成时间较晚,云层厚度明显减小,仅当边界层顶的比湿较大时,有深对流发生,但仍首先发生在干旱下垫面,考虑贯穿对流在边界层顶引起的较强冷却作用,云层厚度大于湿润下垫面。 相似文献
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中国东部地区SO2, SO4=和HNO3(g)干沉降速度的季节变化 总被引：5，自引：0，他引：5
使用中国东部及其邻近地区各主要台站１９９２年全年００点和１２点（ＧＭＴ）地面及探空资料，由中尺度气象预报模式ＭＭ４产生中国东部地区地面以上大约４０ｍ高度（最低模式层）处二维温度、湿度和风场，使用污染物干沉降模块及该地区下垫面类型资料，计算出了该地区ＳＯ２，ＳＯ＝４和ＨＮＯ３（ｇ）全年干沉降速度的区域分布和季节变化。结果表明，由于受气象条件和下垫面类型的综合影响，３种污染物的干沉降速度有明显的变化。对ＳＯ２，全年区域平均极小值为０．０８８ｃｍ／ｓ，极大值为１．２７５ｃｍ／ｓ，平均值为０．４３０ｃｍ／ｓ；对ＳＯ＝４，分别为０．０１４ｃｍ／ｓ，０．２８７ｃｍ／ｓ和０．１１８ｃｍ／ｓ；对ＨＮＯ３（ｇ），分别为０．０６０ｃｍ／ｓ，５．２５０ｃｍ／ｓ和１．１２３ｃｍ／ｓ。ＳＯ２干沉降速度极大值分布在巴丹吉林沙漠和腾格里沙漠一带，对ＳＯ＝４和ＨＮＯ３（ｇ），除在上述沙漠地带有一极大值区域外，在靠近四川的云贵高原尚有另一极大区。对１９９２年全年来说，ＳＯ２和ＨＮＯ３（ｇ）干沉降速度极大值均出现在七月份，分别为０．５５２ｃｍ／ｓ和１．５１８ｃｍ／ｓ；而对ＳＯ＝４，干沉降速度极大值出现在九月份，其值为０．０９６ｃｍ／ｓ。这些值 相似文献
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A number of remotely sensed land cover datasets with spatial resolutions ~〈 1 km have recently become available or are in the process of being mapped. The application of these higher resolution and more up-to-date land cover datasets in chemical transport models （CTMs） is expected to improve the simulation of dry deposition and biogenic emissions of non-methane volatile organic compounds （NMVOCs）, which affect ozone and other secondary air pollutants. In the present study, we updated the land cover dataset in the nested-grid GEOS-Chem CTM with the 1 km resolution GLC2000 land cover map and examined the resulting changes in the simulation of surface ozone and sulfate over China in July 2007. Through affecting the dry deposition velocities of ozone and its precursors, using GLC2000 in the dry deposition module can decrease the simulated surface ozone by 3% （up to 6 ppb） over China. Simulated surface sulfate shows an increase of 3% in northwestern China and a decrease of 1% in northern China. Applying GLC2000 in the biogenic emissions of the NMVOC module can lead to a 0.5--4.5 ppb increase in simulated surface ozone over East China, mainly driven by the larger cove~：age of broadleaf trees in East China in the GLC2000 dataset. Our study quantifies the large sensitivity to land cover dataset~ with different spatial resolutions and time periods of simulated secondary air pollutants over China, supporting ongoing research efforts to produce high resolution and dynamically updated land cover datasets over China, as well as for the globe. 相似文献
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This paper presents dry deposition flux and deposition velocity of atmospheric particles on white marble and red stone at Dayalbagh, a suburban site of semi arid region, which is 10 km away from the industrial sector of the Agra city where due to agricultural practices vegetation predominates. The wind speed at Agra is mostly in the range of 1–2 m s–1. The atmospheric calm conditions at Agra in summer, monsoon, and winter seasons are 47%, 35%, and 76%, respectively. Industrial areas of the city are away from Dayalbagh and are located in the NE, E, SE, and SW sectors. The main industrial activities, which are in operation in Agra city and its outskirts, are foundry and forging industry. The other industrial activities in Agra are rubber processing, lime oxidation and pulverization, chemicals, engineering and brick refractory kilns. Dry deposition samples were collected on dry days on white marble and red stone (0.224 m × 0.224 m × 0.02 m) using surface washing method. Both slabs were fixed to an iron stand (1.5 m height) at an angle of about 80 from the horizontal and exposed for 24 h on the roof of the faculty building. The order of deposition flux on white marble is NH4+ > Mg2+ > Ca2+ > Na+ > Cl– > K+ > NO3– > SO42– > F– and that on red stone is NH4+ > Mg2+ > Ca2+ > SO42– > Na+ > NO3– > K+ > F– > Cl–. Average dry deposition flux of major ions varies from 3.4 to 128.5 M m–2 d–1. The sum of major cations on white marble and red stone are 516.4 and 450.4 eq m–2 d–1, respectively while sum of major anions are 425.3 and 400.4 eq m–2 d–1 on white marble and red stone, respectively. Higher deposition of all ions was observed when wind blows from NE as most of the Agra Iron foundries and Ferozabad glass industries lie in this direction. The mean values of dry deposition velocity of ions vary between 0.22 cm s–1 to 1.49 cm s–1. Deposition velocity for all ions is higher on white marble than red stone inspite of rougher surface of red stone as compared to white marble. This could be due to the chemical nature of white marble, which is made of dolomite and hence adds significant amount of ions by dissolution during washing. Seasonally the deposition velocity was highest in winter. 相似文献
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Chen Panqin 《大气科学进展》1987,4(3):323-331
On the basis of the data of concentrations as well as wind and temperature, simultaneously observed in the north suburb of Beijing, measurements have been made of the dry deposition velocities of suspended particles. Results show that, over such an environment, the dry deposition velocities for suspended par-ticles vary from 0.15 to 10.62 cm s-1, which are comparable with those over forests, that the average surface resistance in the transfer process of particles is about four times as large as the aerodynamic resis-tance, and that the dry deposition velocity is well related to the frictional velocity in terms of positive cor-relation function. 相似文献
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Dry deposition and air concentration samples were collected from July 2004 to May 2005 at a suburban site in Turkey. A water surface sampler (WSS) was used to measure directly the dry deposition flux of particulate polychlorinated biphenyls (PCBs) while a high volume air sampler (HVAS) was employed to collect air samples. Particulate PCB concentrations accounted for 15% of total PCBs (gas + particle phase) at the site. The overall particulate phase PCB flux ranged from 2 to 160 ng m− 2 d− 1 with an average of 46.3 ± 40.6 ng m− 2 d− 1. Forty one PCB congeners were targeted in the samples while twenty one congeners were found to be higher than detection limits in deposition samples. Fluxes for homolog groups ranged between 0.9 (7-CBs) and 21.0 (3-CBs) ng m− 2 d− 1. Measured dry deposition fluxes were lower than the ones usually reported for urban sites. Average PCB dry deposition velocity, calculated using flux values and concurrently measured atmospheric concentrations, was 1.26 ± 1.86 cm s− 1 depended on size distribution of particles, atmospheric PCB concentrations and meteorological conditions. 相似文献
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The total dust column and the dry deposition flux were calculated based on the optical properties that were measured by a shipboard sun photometer POM-01 MKⅡ in a cloud-free and nonfrontal dust condition on 24 April 2006. The total dust column was calculated by using an integration method of the particle size distribution; the mean value was 1.42±0.30 g m-2. A linear correlation between the total dust column and the aerosol optical depth (AOD) with a linear factor of 2.7 g m-2 over the Sahara was applied to calculate the total dust column in this study; the results were lower than these calculated by the integration method. A reasonable factor of 3.2 g m-2 was achieved by minimizing the standard deviation (SD) of the two methods. The two layers model, which includes the deposition processes of turbulent transfer, Brownian diffusion, impaction and gravitational settling over the sea’s surface, was used to calculate the dry deposition flux; the mean value was 5.05±2.49 μg m-2 s-1. A correlation among the total dust column, dry deposition flux, AOD, and effective radius was discussed. The correlation between the total dust column and the AOD was better than that between the total dust column and the effective radius; however, the correlation between the dry deposition flux and the effective radius was better than that between the dry deposition flux and the AOD. 相似文献