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首页> 外文期刊>Forests >Pine Stand Density Influences the Regeneration of Acacia saligna Labill. H.L.Wendl. and Native Woody Species in a Mediterranean Coastal Pine Plantation
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Pine Stand Density Influences the Regeneration of Acacia saligna Labill. H.L.Wendl. and Native Woody Species in a Mediterranean Coastal Pine Plantation

机译:松立架密度会影响金合欢萨尔尼亚吉他的再生。 H.L.Wendl。和地中海沿海杉木种植园的原生木质物种

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摘要

Mediterranean plantations are the most suitable areas to assess vegetation dynamics and competitive interactions between native and exotic woody species. Our research was carried out in a coastal pine plantation (Sicily) where renaturalization by native species ( Pistacia lentiscus L. and Olea europaea var. sylvestris ) and invasion by Acacia saligna (Labill.) H.L.Wendl. simultaneously occur. The regeneration pattern of woody species in the pine understory was evaluated in six experimental plots along a stand density gradient, from 200 to approximately 700 pines per hectare. Both pine stand density and regeneration by native species had a significant negative relationship with Acacia natural regeneration. Olea regeneration was positively correlated with stand density, while Pistacia showed a non-significant relationship. Saplings of both native species were mostly less than 1 m high, whereas approximately 70% of Acacia individuals were higher than 1 m. We found that 400 pines per hectare should be considered a minimum stand density to keep Acacia under control, while favouring the establishment of native species in the understory. The successful control of Acacia requires an integrated management strategy, including different forest interventions according to stand density: thinning, control measures against Acacia , and renaturalization actions.
机译:地中海种植园是评估植被动态和原生和异国情调的木质物种之间的竞争相互作用的地区。我们的研究是在沿海杉木种植园(西西里岛)进行的,其中天然物种(Pistacia Lentiscus L.和Olea Europaea var。Sylvestris)和Acacia Saligna(Labill。)H.L.Wendl的入侵。同时发生。松树林中木质物种的再生模式在六个实验图中,沿着立式密度梯度评估了200至约700个百分之一的每公顷。原生物种的松干密度和再生都与金合欢天然再生具有显着的负面关系。 OLEA再生与支架密度​​呈正相关,而Pistacia表现出非显着的关系。天然物种的树苗大多低于1米,而大约70%的合欢个体高于1米。我们发现每公顷400个松树应被视为最小的立体密度,以防止控制金合欢,同时有利于在林内建立本地物种。成功控制金合欢需要综合管理策略,包括根据立场密度的不同森林干预:稀疏,控制措施对抗合欢,转向化行动。

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