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Assessment and Inventory of Forest Ecosystems Biodiversity: Case Study for Karelian Isthmus of Leningrad Region, Russia

机译:森林生态系统生物多样性评估和清单:俄罗斯列宁格勒地区卡雷利地峡的案例研究

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Regular grid of permanent sample plots (PSP) of ICP-Forests monitoring system was used for forest ecosystems biodiversity assessments and inventory. The supplementary features were added to the PSP structure to conduct biological diversity census: eight sample plots 1 × 1 m for geo-botanical description; two sample plots of 5 × 5 m each for description of the PSP’s undergrowth; one 25 × 25 m plot for coarse woody debris estimations; four soil inventory pits. The total number of PSP amounted to 248. Total data used are as following: 1) 1984 geo-botanical descriptions of vegetation belonging to ground cover layers made on 1 × 1 m sample plots; 2) 496 descriptions of undergrowth on 5 × 5 m sample plots; 3) 178 descriptions of woody debris on 25 × 25 m sample plots; 4) 496 descriptions of soil inventory pits. General statistical indicators characterizing forest land cover diversity were calculated. Statistic indicators of α-diversity for the Karelian Isthmus forest vegetation cover have the following values: 1) m (mean number of species per PSP) = 26 species; 2) σ (standard deviation) = 9.5 species; 3) v (variation coefficient) = 36.5%; 4) Р (deviation amplitude) = 60 – 7 = 53 species. β – diversity of forest ecosystems as well as γ – diversity also was studied on the base of information collected on the same regular grid of sample plots. It appears that sample plots distribution by species diversity gradation is well described by the standard curve of normal distribution for the entire Karelian Isthmus forest (determination coefficient of the curve being 95.2%) as well as for each type of forest. Hence, the criterion (standard) of biodiversity for forest ecosystems can be defined as the mean value of alpha diversity for each forest type group – m; and the standard deviation – σ, as a tool for assessing deviations from the standard. PSP locations are fixed using GPS technology, this allows biodiversity assessments at the same place in the next years for biodiversity trends estimations and consist the frame for systematic biodiversity inventory.
机译:ICP-森林监测系统的永久性样地的规则网格用于森林生态系统生物多样性评估和清查。在PSP结构中增加了补充功能,以进行生物多样性普查:8个样地1×1 m用于地理植物学描述;两张5×5 m的样地,用于描述PSP的灌木丛。一个25×25 m的地块,用于估计粗木屑;四个土壤存货坑。 PSP总数为248。使用的总数据如下:1)1984年在1×1 m样地上对属于地被覆层的植被进行了植物学地理描述; 2)在5×5 m样地上的496种灌木丛的描述; 3)在25×25 m样地上描述了178种木屑; 4)496个土壤存积坑描述。计算了表征林地覆盖多样性的一般统计指标。卡累利阿地峡森林植被覆盖度的α多样性统计指标具有以下值:1)m(每PSP的物种平均数)= 26种; 2)σ(标准偏差)= 9.5种; 3)v(变异系数)= 36.5%; 4)Р(偏差幅度)= 60 – 7 = 53种。还基于在相同样地的规则网格上收集的信息,研究了森林生态系统的β–多样性和γ–多样性。看来,通过整个卡累利阿地峡森林(曲线的确定系数为95.2%)以及每种类型的森林的正态分布标准曲线可以很好地描述按物种多样性等级划分的样地分布。因此,森林生态系统生物多样性的标准(标准)可以定义为每种森林类型组的α多样性的平均值。和标准偏差–σ,作为评估与标准偏差的工具。 PSP的位置使用GPS技术进行固定,从而可以在未来几年中在同一地点进行生物多样性评估,以估算生物多样性趋势,并构成系统生物多样性清单的框架。

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