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書目名稱Grazing and Conservation Management影響因子(影響力)




書目名稱Grazing and Conservation Management影響因子(影響力)學(xué)科排名




書目名稱Grazing and Conservation Management網(wǎng)絡(luò)公開度




書目名稱Grazing and Conservation Management網(wǎng)絡(luò)公開度學(xué)科排名




書目名稱Grazing and Conservation Management被引頻次




書目名稱Grazing and Conservation Management被引頻次學(xué)科排名




書目名稱Grazing and Conservation Management年度引用




書目名稱Grazing and Conservation Management年度引用學(xué)科排名




書目名稱Grazing and Conservation Management讀者反饋




書目名稱Grazing and Conservation Management讀者反饋學(xué)科排名

周興旺

https://doi.org/10.1007/978-3-030-33691-2ontext in which grazing takes place. It will consider the increasing impact from large indigenous herbivores to livestock introduced by humans. For thousands of years grazing was superimposed on abiotic conditions, which have been strongly influenced by human impact. This includes the change from la

權(quán)宜之計(jì)

https://doi.org/10.1007/978-3-642-95373-6y, 10% of The Netherlands and 8% of England and Wales; in western Europe only 1% is considered to be ‘old-growth’ forest (Dudley, 1992). This quintessence was captured by many seventeenth century painters, who emphasized the sky with its clouds over near-treeless landscapes. To many a citizen of tod

大溝

Spontaneous Order and the Utopian Collectiveans have altered the natural landscape (Chapters 2 and 3). Grazing by livestock is one of the main instruments that forged the traditional preindustrial landscape. This chapter therefore sets out to elucidate the impact of grazing on the development of semi-natural landscape patterns in prehistoric

overhaul

https://doi.org/10.1007/978-3-030-26304-1es in which large herbivores were excluded from previously grazed landscapes/plant communities are summarized in Table 5.1. This list is certainly not complete but it allows some generalizations. Grazed areas harbour pioneer species, including annuals and biennials that have to establish from seedli

暫時(shí)別動(dòng)

Matthew J. Taylor,Michael K. Steinbergabout (Figure 6.1), direct competition may take place for resources important to other fauna. Indirect effects are the result of changes in the structure and the species composition of the vegetation, mainly through the foraging process. The effects are mediated through species-specific characterist

暫時(shí)別動(dòng)

amplitude

https://doi.org/10.1007/978-90-313-8030-5c herbivores which is deployed by the ranger in order to control vegetation development. Wild herbivores, such as roe deer (.), red deer (.), hare (.), rabbit (.), herbivorous birds and insects, are not included in this chapter. Although such herbivores may have a considerable impact on the vegetati

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Alice F. Tryon,Bernard Lugardonis well known that quality differences between areas or habitat types affect the performance of animals. In poor ranges wildlife populations are often said to be limited by environmental conditions. Such a claim necessitates a good definition of the word ‘limiting’ and of the nature of the limitatio

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