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Soil organic matter formation and sequestration during floodplain forest succession.

机译:漫滩森林演替过程中土壤有机质的形成和固存。

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Successional changes in soil organic matter (SOM) formation and sequestration were studied at the Savannah River Site, South Carolina. Four sites were studied, three of which were in various stages of recovery from 30--35 years of impact due to thermal effluent discharge during nuclear reactor operations. The fourth was a minimally disturbed reference site. Forest floor mass (as well as C, N, and P pools) increased rapidly during early secondary succession, with a maximum of 657 g/m2 and decreasing to 338 g/m 2 in late succession. Percent herbaceous material of the forest floor declined during succession from 74% in an early stage to less than 1% in the latest seral stage. Conversely, the amount of woody foliage increased from 6.7% to more than 70% in late succession. Measures of the degree of transformation of forest floor litter to SOM using the lignocellulose index did not differ between stages of succession, suggesting that any effect by the forest floor on the increase in soil C and N was a function of forest floor mass only. Percent lignin and cellulose of the forest floor were similar between stages, ranging from 13.8--16.3%, and 30.4--32.5%, respectively. C:N ratios of the forest floor were similar throughout succession, ranging from 41 to 48, as were lignin:N ratios, which ranged between 12 and 14.; Carbon and N content of the mineral soil increased with successional stage of the floodplain chronosequence, from 15.6 kg C/m2/0.7 m in the earliest stage to 56 kg C/m2 in the latest, and 0.6 to 3.6 kg/m2 for N. Regression analyses indicated that it may take over 50 years for C and N levels in the upper 0.7 m of mineral soil to reach 75% of that of the reference site. C:N ratios in mineral soil returned to pre-disturbance levels after about one decade. Analysis of the distribution of soil aggregates across four size classes suggested that soil structure was disrupted by the disturbance, producing a greater proportion of microaggregates (53--250 mum) in early stages. Also, small macroaggregates (250--2000 mum) were accruing C and N more slowly than other size fractions, suggesting that small macroaggregates harbored a fraction less resilient to disturbance than other fractions. The formation of soil aggregate structure, which may facilitate the accrual of C and N, was occurring slowly. SOM dynamics in small macroaggregates and microaggregates were examined further by using physical fractionation procedures to produce twenty and sixteen size-density fractions, respectively. For small macroaggregates and microaggregates, disturbed sites contained significantly smaller amounts of C and N in the 2.0--2.2 g/cm3 density fraction of the 25 mum size classes, also indicating the possibility of a fraction that is more sensitive to soil disturbance.
机译:在南卡罗来纳州的萨凡纳河站点研究了土壤有机质(SOM)形成和固存的连续变化。研究了四个地点,其中三个因核反应堆运行过程中的热废水排放而处于从30--35年的撞击中恢复的不同阶段。第四个是受干扰最小的参考站点。在次生演替早期,森林地表质量(以及C,N和P池)迅速增加,最大值为657 g / m2,在后期演替中降低至338 g / m 2。林地中草本材料的百分比在演替过程中从早期的74%下降到最近的耕作阶段的不足1%。相反,在后期演替中,木质叶子的数量从6.7%增加到70%以上。使用木质纤维素指数衡量林地凋落物转化为SOM的程度在演替阶段之间没有差异,这表明林地对土壤碳和氮增加的任何影响仅是林地质量的函数。各阶段森林地层木质素和纤维素的百分比相似,分别为13.8--16.3%和30.4--32.5%。在整个演替过程中,森林地面的C:N比值​​相似,从41到48,木质素:N比值在12到14之间。矿质土壤中的碳和N含量随着洪泛期次序列的演替阶段而增加,从最早的15.6 kg C / m2 / 0.7 m到最近的56 kg C / m2,N的0.6到3.6 kg / m2。回归分析表明,上部0.7 m矿质土壤中的碳和氮水平可能需要50年以上才能达到参考点的75%。大约十年后,矿质土壤中的C:N比值​​恢复到扰动前的水平。对四种规模类别的土壤团聚体分布的分析表明,土壤结构受到干扰的破坏,在早期阶段产生了更大比例的微团聚体(53--250微米)。此外,小型大型聚集体(250--2000毫米)的C和N积累速度比其他大小的分数要慢,这表明小型大型聚集体的抗干扰能力要弱于其他分数。可能促进碳和氮积累的土壤团聚体结构形成缓慢。通过使用物理分级分离程序分别产生二十个和十六个粒度密度分数,进一步检查了小型大型聚集体和微小聚集体中的SOM动力学。对于较小的大型骨料和微骨料,在小于25微米大小等级的2.0--2.2 g / cm3密度分数中,受干扰的位点含有显着较少的C和N,这也表明存在对土壤扰动更敏感的分数的可能性。

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