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Characterization of the water soluble soil organic pool following the rewetting of dry soil in a drought-prone tallgrass prairie

机译:干旱多草草原上干土重新湿润后的水溶性土壤有机池特征

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To better understand the nature of the C flush that follows the rewetting of dry soil, we chemically characterized the water soluble pools following rewetting of soil dried to several different water potentials. To assess the impact that historical soil water status has on the size of the rewetting labile soluble pool, a laboratory water stress gradient was applied to soils that were collected from drought-prone and irrigated tallgrass prairie soils. In the laboratory, soils were either incubated at -33 kPa or dried steadily over a 0.6, 1, 2, or 3 day period to -1.5, -4, -15, and -45 MPa respectively. On the 4th day, samples were wetted back to -33 kPa and immediately assayed for soluble, microbial, or respiratory pools of carbon. After extraction, samples were also assayed using NMR, GC-MS, and LC-MS to assess carbohydrate, amino acid, osmolyte and sugar pools. The greater the degree of drying before rewetting was associated with greater concentrations of microbial, soluble and respiratory pools of carbon, increasing by 50, 400 and 250%, respectively, in the most water stressed compared to continuously moist soil. Compared to drought-prone soils, the amount of soluble C released as a result of rewetting was 30 to 50% greater in soils that were irrigated for 11 years. The pool of organics was not completely characterized and only small amounts of TBDMS and TMS derived compounds accounting for 2-4% of the soluble C pool were detected. In contrast, oligosaccharides constituted approximately 20-25% of the sample C. Our results suggest that the flush of C following wetting of a dry soil is not dominated by common microbial osmolytes (e.g. proline, glycine betaine, ectoine, glycerol, mannitol, trehalose). In light of this finding more research is needed to better understand the adaptations that microbial communities utilize to respond to the rewetting of dried soil.
机译:为了更好地了解干土壤重新湿润后冲洗的性质,我们对干燥后的土壤重新湿润至几种不同的水势后的化学性质进行了化学表征。为了评估历史土壤水分状况对再润湿不稳定的可溶性库的大小的影响,将实验室水分胁迫梯度应用于从容易干旱和灌溉的高草草原土壤中收集的土壤。在实验室中,将土壤以-33 kPa孵育,或在0.6、1、2或3天的时间内稳定干燥至分别为-1.5,-4,-15和-45 MPa。在第4天,将样品弄湿至-33 kPa,并立即分析可溶性碳,微生物碳或呼吸碳。提取后,还使用NMR,GC-MS和LC-MS分析样品,以评估碳水化合物,氨基酸,渗透压和糖池。与持续潮湿的土壤相比,在水分最多的情况下,重新润湿前的干燥程度越高,微生物,可溶性碳和呼吸碳的浓度就越高,分别在最高水分胁迫下分别增加了50%,400%和250%。与易干旱的土壤相比,在灌溉11年的土壤中,由于再润湿而释放的可溶性碳增加了30%至50%。有机物库尚未完全鉴定,仅检测到少量TBDMS和TMS衍生的化合物,占可溶性C库的2-4%。相比之下,低聚糖占样品C的约20-25%。我们的结果表明,在干燥土壤润湿后C的冲洗不是由常见的微生物渗透剂(例如脯氨酸,甘氨酸甜菜碱,ectoine,甘油,甘露醇,海藻糖)主导的。 )。鉴于这一发现,需要进行更多的研究以更好地理解微生物群落对干燥土壤的重新润湿所起的适应作用。

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