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首页> 外文期刊>Arctic: Journal of the Arctic Institute of North America >Condition, potential recovery rate, and productivity of lichen (Cladonia spp.) ranges in the Finnish reindeer management area
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Condition, potential recovery rate, and productivity of lichen (Cladonia spp.) ranges in the Finnish reindeer management area

机译:芬兰驯鹿管理区的地衣(Cladonia spp。)的状况,潜在的恢复率和生产力

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The focus of the work was to investigate dependency between reindeer density and lichen (Cladonia spp.) ranges in the Finnish semidomesticated reindeer management area. Secondly, we formed a model on the recovery rate of ungrazed woodland lichen ranges (29 sites) after forest fires to evaluate the potential productivity and time needed for Finnish lichen ranges to recover at optimal production. During 1974–95, 59% of the variation in mean semidomesticated reindeer density (range: 0.7– 3.0 reindeer/km2 of the total land area) among the reindeer herding districts in Finland was explained by the proportion of land area covered by lichen ranges in these districts. Reindeer densities were highest in the districts where lichen ranges covered 20% to 30% of the area. Reindeer density on the total land area did not explain the condition of lichen ranges, but 58% of the condition was explained by the reindeer density on the lichen ranges. A condition level for lichen ranges of 1000 kg dry matter per hectare (d.m./ha) of lichen biomass can be considered adequate to ensure survival of reindeer and continued production of lichen. To maintain this level within the sedentary Finnish grazing system, winter reindeer densities on lichen ranges must remain below 5– 7 reindeer/km2. According to our model, the maximum amount of living lichen in the woodland lichen stand at the climax stage is on average about 7000 kg d.m./ha. The maximum annual yield of lichen (175 kg d.m./ha) is produced by lichen stands that contain 2600–2800 kg d.m./ha of living lichen. Using our model and our 1995–96 data, we calculated that the average lichen biomass on lichen ranges in the Finnish reindeer management districts was 13.0% of this optimum, and the average lichen production was 36% of the possible maximum annual yield. Our model indicates that the Finnish lichen ranges would have to remain ungrazed for an average of 18 years to recover to maximum production levels. However, the average time needed for the lichen ranges to recover to the level of 1000 kg lichen d.m./ha, would be only about 7 years.
机译:工作重点是调查芬兰半驯化驯鹿管理区的驯鹿密度与地衣(Cladonia spp。)范围之间的依赖性。其次,我们针对森林大火后未磨擦的林地地域(29个地点)的恢复率建立了模型,以评估芬兰地衣以最佳产量恢复所需的潜在生产力和时间。在1974-95年间,芬兰驯鹿放牧区的平均半驯化驯鹿密度(范围:总陆地面积0.7-3.0驯鹿/ km2)中59%的变化是由地衣覆盖的土地面积比例解释的。这些地区。在地衣覆盖面积占20%至30%的地区,驯鹿密度最高。总土地面积上的驯鹿密度不能解释地衣范围的条件,但是58%的条件由地衣范围上的驯鹿密度来解释。每公顷地衣生物量1000千克干物质的地衣条件水平可以认为足以确保驯鹿的生存和继续生产地衣。为了在久坐的芬兰放牧系统中维持这一水平,地衣范围内的冬季驯鹿密度必须保持在5-7驯鹿/平方千米以下。根据我们的模型,高潮期林地地衣林中最高的活地衣量平均约为7000 kg d.m./ha。包含2600–2800 kg d.m./ha的活动地衣的地衣架可产生最大的地衣年产量(175 kg d.m./ha)。使用我们的模型和1995-96年的数据,我们计算出芬兰驯鹿管理区地衣范围内的平均地衣生物量为该最佳值的13.0%,平均地衣产量为可能的最大年产量的36%。我们的模型表明,芬兰地衣范围必须平均保持18年不变,才能恢复到最高产量。但是,地衣恢复到每公斤1000公斤地衣水平所需的平均时间仅为7年左右。

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