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Soil Amendment Increases Tree Seedling Growth but Reduces Seedling Survival at a Retired Gravel Mine

机译:土壤改良剂增加了退休砾石矿山树木的幼苗生长,但减少了幼苗的存活

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Restoring forest vegetation within denuded settings requires identifying the abiotic factors that limit plant establishment (Bradshaw 1997, Whisenant 1999). In heavily disturbed sites such as quarries and gravel pits that have been denuded of native soils, degraded soil processes may limit planted tree seedling survival or growth (Williamson et al. 2011). To improve vegetation establishment on denuded sites, soil amendments are commonly used to manipulate soil fertility (Biederman and Whisenant 2011a, Hough-Snee et al. 2011a), introduce organic matter, soil microorganisms, or propagules (Sinnett et al. 2008, Hough-Snee et al. 2012), or to create heterogeneous microhabitats (Biederman and Whisenant 2011b, Hough-Snee et al. 2011b) that improve plant survival. In forest restoration, amendments that facilitate soil development can lead to increased plant survival and growth (Ortiz et al. 2011). Specifically, amendments that increase soil carbon and nitrogen have been shown to improve planted tree seedling growth (Wilson-Kokes et al. 2013). Soil amendments for denuded sites are typically designed to increase planted tree growth so that seedlings may outcompete early seral vegetation and survive to maturity (Bradshaw 1997). In this study we examined how soil amendments change soil properties at a highly disturbed site and how these amendments impact the growth and survival of three early successional tree species. We tested two sets of hypotheses: 1. Soil amendment will increase soil carbon and nitrogen, C to N ratio, soil moisture, and decrease soil bulk density. 2. The amendment-driven increase in soil fertility will increase the survival and growth of planted black cottonwood (Populus balsamifera), red alder (Alnus rubra) and Douglas fir (Pseudotsuga menziesii) seedlings relative to unamended seedlings.
机译:在裸露的环境中恢复森林植被需要确定限制植物生长的非生物因素(Bradshaw 1997,Whisenant 1999)。在严重扰乱了采石场和砾石坑的地方,这些地方已经剥夺了原生土壤,退化的土壤过程可能会限制种植的树木幼苗的存活或生长(Williamson等,2011)。为了改善裸露地点的植被,通常使用土壤改良剂来控制土壤肥力(Biederman和Whisenant 2011a,Hough-Snee等人2011a),引入有机物,土壤微生物或繁殖体(Sinnett等人2008; Hough- Snee等人,2012年),或创建异种微生境(Biederman和Whisenant 2011b,Hough-Snee等人2011b),以提高植物的存活率。在森林恢复中,促进土壤发育的改良剂可导致植物存活和生长增加(Ortiz等,2011)。具体而言,已表明增加土壤碳和氮的改良剂可改善种植的树木幼苗的生长(Wilson-Kokes等,2013)。裸露地的土壤改良剂通常旨在增加树木的生长,从而使幼苗能够胜过早期的草木植被,并能存活到成熟(Bradshaw 1997)。在这项研究中,我们研究了土壤改良剂如何在高度受干扰的地点改变土壤特性,以及这些改良剂如何影响三种早期演替树种的生长和存活。我们测试了两组假设:1.土壤改良剂会增加土壤碳和氮,碳氮比,土壤湿度并降低土壤容重。 2.修正驱动的土壤肥力增加将相对于未改良的秧苗,增加种植的黑杨(Populus balsamifera),赤al木(Alnus rubra)和花旗松(Pseudotsuga menziesii)的存活和生长。

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