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首页> 外文期刊>Weed Technology >Revegetation Strategies After Saltcedar (Tamarix spp.) Control in Headwater, Transitional, and Depositional Watershed Areas1
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Revegetation Strategies After Saltcedar (Tamarix spp.) Control in Headwater, Transitional, and Depositional Watershed Areas1

机译:水源,过渡带和沉积流域地区的柳杉(Tamarix spp。)控制后的植被恢复策略 1

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摘要

The exotic saltcedar occupies headwater, transitional, and depositional watershed portions, and revegetation strategies can be quite different depending on these locations. Regardless of specific socioeconomic or biological needs (or both), sites must often be revegetated after control to avoid reinfestation or invasion by other exotic species. Where natural riparian hydrologic processes continue to function, natural regeneration can be used as an effective restoration mechanism. However, in altered river systems, harsh environmental site characteristics may occur that severely limit revegetation potential after control, particularly in depositional areas. Because of high costs associated with saltcedar control, revegetation, and follow-up management, specific treatment areas should be evaluated and prioritized based on revegetation potential. Specific consideration should be given to the establishment of sustainable plant communities for long-term exclusion of saltcedar and other exotics.
机译:异国情调的柳杉占据了源头,过渡和沉积的分水岭部分,根据这些位置,重新植被的策略可能会完全不同。无论特定的社会经济或生物学需求(或两者都有),都必须在控制后经常对植被进行重新植被,以避免再次受到其他外来物种的侵扰。在自然河岸水文过程继续起作用的地方,自然再生可以用作有效的恢复机制。但是,在变化的河流系统中,可能会出现恶劣的环境点特征,从而严重限制了控制后的植被恢复潜力,特别是在沉积区。由于与盐杉控制,植被恢复和后续管理相关的高成本,应根据植被恢复潜力对特定的治疗区域进行评估并确定优先级。应特别考虑建立可持续的植物群落,以长期排除盐杉和其他外来植物。

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