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1.
作者研究三维变系数抛物方程 Douglas交替方向隐格式的稳定性和收敛性。采用 H1能量估计方法 ,证明格式按离散 H1范数是绝对稳定的 ,并且收敛阶为 O(Δ t2 + h2 )  相似文献   
2.
Emission rates of biogenic volatile organic compounds emitted by the forests were estimated for five geographical regions as well as for all Switzerland. Monoterpene and isoprene emissions rates were calculated for each main tree species separately using the relevant parameters such as temperature, light intensity and leaf biomass density. Biogenic emissions from the forests were found to be about 23% of the total annual VOC emissions (anthropogenic and biogenic) in Switzerland. The highest emissions are in July and lowest in January. Calculations showed that the coniferous trees are the main sources of the biogenic emissions. The major contribution comes from the Norway spruce (picea abies) forests due to their abundance and high leaf biomass density. Although broad-leaved forests cover 27% of all the forests in Switzerland, their contribution to the biogenic emissions is only 3%. Monoterpenes are the main species emitted, whereas only 3% is released as isoprene. The highest emission rates of biogenic VOC are estimated to be in the region of the Alps which has the largest forest coverage in Switzerland and the major part of these forests consists of Norway spruce. The total annual biogenic VOC emission rate of 87 ktonnes y–1 coming from the forests is significantly higher than those from other studies where calculations were carried out by classifying the forests as deciduous and coniferous. The difference is attributed to the high leaf biomass densities of Norway spruce and fir (abies alba) trees which have a strong effect on the results when speciation of trees is taken into account. Besides the annual rate, emission rates were calculated for a specific period during July 4–6, 1991 when a photochemical smog episode was investigated in the Swiss field experiment POLLUMET. Emission rates estimated for that period agree well with those calculated for July using the average temperatures over the last 10 years.  相似文献   
3.
采用有机溶剂与蒸馏水混和浸提杉木枯枝落叶腐解9个月后化感物质,应用杉木种子发芽试验进行生物检测.结果表明:杉木枯枝落叶腐解9个月后,杉木枯枝落叶中的弱极性化感物质对绝对发芽率、绝对发芽势、胚根长、胚轴长及干物质量等指标表现为抑制作用,对鲜物质量则表现为轻微的促进作用;极性化感物质对杉木种子发芽各指标均等表现为抑制作用.腐解土中的弱极性化感物质对杉木种子发芽各指标均表现为抑制作用,极性化感物质对绝对发芽率、绝对发芽势、胚轴长及干物质量等表现为抑制作用,但对胚根长、鲜物质量表现为促进作用.  相似文献   
4.
腐解9个月后杉木枯枝落叶化感物质对杉木的化感作用   总被引:5,自引:0,他引:5  
采用有机溶剂与蒸馏水混和浸提杉木枯枝落叶腐解9个月后化感物质,应用杉木种子发芽试验进行生物检测.结果表明:杉木枯枝落叶腐解9个月后,杉木枯枝落叶中的弱极性化感物质对绝对发芽率、绝对发芽势、胚根长、胚轴长及干物质量等指标表现为抑制作用,对鲜物质量则表现为轻微的促进作用;极性化感物质对杉木种子发芽各指标均等表现为抑制作用.腐解土中的弱极性化感物质对杉木种子发芽各指标均表现为抑制作用,极性化感物质对绝对发芽率、绝对发芽势、胚轴长及干物质量等表现为抑制作用,但对胚根长、鲜物质量表现为促进作用.  相似文献   
5.
不同栽杉代数土壤抗蚀性的变化   总被引:7,自引:2,他引:5  
采用标准地定位研究方法对杂木林及1代,2代,3代和4代杉木人工林土壤颗粒,土壤团聚体组成进行比较分析,结果表明:杂木要受人为干扰少,土壤颗粒及土壤团聚体组成较好,抗蚀性最好;但1代,2代,3代和4代分别是在杂木林及前1代林的采伐迹地上经再度干扰建立起来的,土壤结构破坏率加大,土壤团聚体稳定性减小,因而随着杉木林取代杂木林及杉木连栽代数增加,土壤抗蚀性减弱。  相似文献   
6.
 为估算树木在不同生长环境下的生长量及评价树木与环境之间的相互关系,本文以幼龄杉木为对象,从个体尺度上,根据形态结构生长发育规律,定义了幼龄杉木生长的基本单元,耦合用于表达树木形态发育的L-系统和生理生态模型,形成了L-系统的杉木结构-功能模型。在LSTree软件基础上,集成光合作用、生物量分配等模型,扩展了冠层光合有效辐射(PAR)的空间分布模拟,计算每个叶片上分布的PAR值,为光合作用模型提供核心参数。以福州3-4年生杉木的生长盛期为例,计算不同时刻净光合速率,从而计算各生长阶段的生物量,再把生物量分配到各器官。在生物量驱动下,树木形态结构发生变化,通过迭代,实现生物量驱动下的树木动态生长模拟。净光合速率估算结果与已有相关研究对比,比较合理。这种方法可定量分析、解释植物与环境之间关系。  相似文献   
7.
不同年龄杉木人工林土壤无机氮比较研究   总被引:1,自引:0,他引:1  
在福建南平杉木林中心产区,选取11、21、28、40、88年生杉木人工林以及采伐迹地、杂木林为研究对象,研究不同年龄杉木林土壤无机氮的差异.结果表明:不同年龄杉木林土壤NH4^+-N含量差异显著,以21年生的杉木人工林最高(11.91±0.43mg·kg^-1),其他的为88年生的(8.33±0.38mg·kg^-1)〉28年生的(8.19±0.25mg·kg^-1)〉11年生的(5.65±0.17mg·kg^-1)〉40年生的(5.63±0.38mg·kg^-1);NO3^--N含量较低(3.15~4.11mg·kg^-1),且没有显著差异,这与杉木林所处的生长阶段、土壤理化性质有关.杉木林取代杂木林后,NH4^+-N和NO3^--N含量都有所下降;采伐迹地土壤NH4^+-N(19.74±1.44mg·kg^-1)和NO3^--N(18.05±0.72mg·kg^-1)含量远高于88年生的杉木林,分别是88年生的2.37和4.60倍.本地区无机氮含量较低,NH4^+-N占无机氮的比例为60.0%~74.3%,NH4^+-N为无机氮的主要形态.  相似文献   
8.
Abstract

The dynamic properties of rainfall interception were investigated at three growth stages in Chinese fir plantations. The results showed that the annual interception ratio was significantly higher in mature stands than in young stands. For a storm event, interception rainfall amount increased with increasing rainfall, but interception ratio decreased. In contrast to dry season conditions, the interception amount was high in the wet seasons, while the interception ratio was low. The rates of change in interception ratio were extremely rapid in small rainfall events. There was little stemflow in Chinese fir forests due to the pyramid-shaped crowns and thick rough bark of the trees. The power model was suitable to describe the interception process for an individual rainfall event for stands of any age. Our results indicate that the interception process varied for stands of different ages in Chinese fir plantations due to contrasting canopy structures.  相似文献   
9.
《自然地理学》2013,34(3):185-204
This paper investigates the effects of spruce budworm (Choristoneura fumiferana) on balsam fir (Abies balsamea) and white spruce (Picea glauca) at Itasca State Park in northwestern Minnesota. We studied the species composition, age structure, and radial growth patterns in tree rings along five belt transects at sites infested with spruce budworm. Our objectives were to: (1) discover when the latest spruce budworm outbreak started; (2) determine whether tree growth was similarly reduced in earlier decades, suggesting earlier spruce budworm outbreaks; and (3) test whether radial tree growth and the start of the outbreak(s) were correlated with climate. We used the computer program OUTBREAK to determine that the current spruce budworm infestation began to reduce tree growth in the 1990s, before it was detected by park officials in 2001. The tree-ring record indicated that growth of the host-species trees was periodically reduced at all sites prior to the 1990s. We found no consistent relationship between temperature/precipitation and the initiation of spruce budworm outbreaks, as reconstructed by the OUTBREAK program, at the southwestern edge of the distribution of balsam fir. The Palmer Drought Severity Index, however, was positive (i.e., wetter-than-normal conditions) before increased spruce budworm activity at all sites. Outbreaks are related to climatic conditions, but they also depend on other factors such as the availability of sufficient food for the spruce budworm.  相似文献   
10.
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