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Fine root biomass and its relationship to evapotranspiration in woody and grassy vegetation covers for ecological restoration of waste storage and mining landscapes

机译:木本和草木植被覆盖区细根生物量及其与蒸散量的关系,用于废物存储和采矿景观的生态恢复

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摘要

Production and distribution of fine roots (≤2.0 mm diameter) are central to belowground ecological processes. This is especially true where vegetation serves as a pump to prevent saturation of soil and possible drainage of excess water into or from potentially toxic waste material stored underground or in mounds aboveground. In this study undertaken near Sydney in Australia, we determined fine root biomass and evapotranspiration (ET) on a waste disposal site restored with either a 15-year-old grass sward or plantations of mixed woody species that were either 5 years old (plantation-5) with a vigorous groundcover of pasture legumes and grasses, or 3 years old (plantation-3) with sparse groundcover. These sites were compared with nearby remnant woodland; all four were located within 0.5-km radius at the same site. Ranking of fine root biomass was in the order woodland (12.3 Mg ha⁻¹) > plantation-5 (8.3 Mg ha⁻¹) > grass (4.9 Mg ha⁻¹) > plantation-3 (1.2 Mg ha⁻¹) and was not correlated with nutrient contents in soil or plants, but reflected the form and age of the vegetation covers. Trends in root length density (RLD) and root area index (RAI) followed those in root biomass, but the differences in RAI were larger than those in biomass amongst the vegetation covers. Annual ET in the dry year of 2009 was similar in the three woody vegetation covers (652–683 mm) and was at least 15% larger than for the grass (555 mm), which experienced restrained growth in winter and periodic mowing. This resulted in drainage from the grass cover while there was no drainage from any of the woody vegetation covers. In plantation-5, root biomass, RAI and RLD were reduced in the rain shadow side of the tree rows. Similarly, the amount and depth of rooting in the groundcover were reduced close to the trees compared to midway between rows. Differences in the root variables were larger than those in ET, which suggested that more roots were produced than were needed for water uptake and/or presence of considerable amounts of necromass. We conclude that vegetation covers, such as plantation-5 consisting of widely spaced trees and a heavy groundcover containing winter-active pasture legumes, will promote year-round water-use with a reduced risk of deep rooting that could breach buried wastes. This function could be sustained through progressive thinning of trees to account for not more than 25% of the whole canopy cover; this will minimize competition for limited soil-water and thereby constrain deep rooting as vegetation ages and attains climax.
机译:细根(直径≤2.0毫米)的生产和分布是地下生态过程的核心。在植被充当泵防止土壤饱和和防止多余的水排入地下或地下土堆中的有毒废物或从中排出时,尤其如此。在澳大利亚悉尼附近进行的这项研究中,我们确定了用15年草皮或5年龄混合木本物种种植后恢复的废物处理场的细根生物量和蒸散量(ET)。 5)带有强烈的牧草和草的地被植物,或3岁(种植3年)的稀有地被植物。将这些地点与附近的剩余林地进行了比较;所有这四个地点都位于同一地点的0.5公里半径内。细根生物量的排列顺序是林地(12.3 Mg ha¹)>人工林5(8.3 Mg ha¹)>草(4.9 Mg ha¹)>人工林3(1.2 Mg ha¹),并且与土壤或植物中的养分含量无关,但反映了植被覆盖的形式和年龄。根系生物量的根长密度(RLD)和根系面积指数(RAI)的趋势紧随其后,但植被覆盖度的RAI差异大于生物量。在三个木质植被覆盖层(652-683毫米)中,2009年干旱年份的年ET相似,比草(555毫米)大15%,后者在冬季和定期修剪时生长受到限制。这导致了草覆盖层的排水,而任何木质植被的覆盖层都没有排水。在人工林5中,树行的雨影侧根生物量,RAI和RLD减少。同样,与行之间的中途相比,靠近树木的地被植物生根的数量和深度也减少了。根变量的差异大于ET中的差异,这表明产生的根超过了吸水和/或大量坏死瘤所需的根。我们得出的结论是,植被覆盖物(例如种植园5)由宽阔的树木和厚重的地被植物(包括冬季活跃的牧草豆科植物)组成,将促进全年用水,并减少可能破坏掩埋垃圾的深根风险。可以通过逐渐变薄树木来维持这种功能,使其不占整个树冠覆盖的25%;这将最大限度地减少对有限土壤水的竞争,从而随着植被的老化和达到高潮而限制深根。

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