首页> 外文期刊>Eurasian Soil Science >Mineralization of organic-matter labile fragments in the humus-accumulative horizon of soddy-podzolic soil.
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Mineralization of organic-matter labile fragments in the humus-accumulative horizon of soddy-podzolic soil.

机译:泥泞-积土土壤中腐殖质积累层中有机物不稳定碎片的矿化作用。

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The mineralization rate of the 14C-labeled organic matter (OM) in the humus-accumulative AE horizon of a soddy-podzolic soil was determined in a laboratory experiment. The labeling was performed in a field experiment when microamounts of 14C-labeled glucose, glycine, and uracil were added to tree waste in sacks embedded in the upper layer of the forest litter. Samples containing 14C were taken from the AE horizon (above which the sacks with the labeled material were placed) 7 and 20 months after the beginning of the experiment. The soil samples were wetted to a water content corresponding to ~80% of the total water capacity and placed in hermetic vessels containing vials with a periodically renewed alkali solution. The incubation was performed at room temperature for 3.5 months; the alkali solutions in the vials were replaced and titrated 12 times during this period. Mineralization curves were plotted from the amounts of carbon dioxide absorbed by a 0.3 N NaOH solution, which were calculated for each time interval; its 14C content was determined by the scintillation method. The experimental treatments also included the determination of the OM mineralization rate in material from the AE horizon pretreated with a heavy liquid or a heavy liquid and a 0.1 N NaOH solution. The differences between the mineralization rates of the labeled organic matter applied to the soil in the form of glucose, glycine, and uracil under the field conditions after the interaction for 7 and 20 months were revealed. The changes in the mineralization rate after the successive extraction of the labile organic matter with a heavy liquid and a 0.1 N NaOH solution were studied. It was shown that the transformation of the labeled low-molecular-weight organic compounds in the soil over 20 months included their strong inclusion into the humus composition, which was confirmed by the similar values of the mineralization constants of the native and 14C-labeled OM. In addition, the treatments with the heavy liquid or the heavy liquid and the NaOH solution had almost identical effects on the mineralization of the native and 14C-labeled OM. The mineralization constants of the native and 14C-labeled OM in the samples taken after 7 months of the field experiment differed significantly.Notes Translated from Pochvovedenie (2012) 12, 1259-1268 (Ru).
机译:通过实验室实验确定了腐殖质土壤中腐殖质积累的AE层中 14 C标记的有机物(OM)的矿化率。标记是在田间实验中进行的,方法是将少量 14 C标记的葡萄糖,甘氨酸和尿嘧啶添加到森林垃圾上层中埋入的麻袋中的树木废弃物中。在实验开始后的7个月和20个月,从AE地平线(放置有标记材料的麻袋上方)中采集了包含 14 C的样品。将土壤样品润湿至相当于总水容量约80%的水含量,然后将其放入装有小瓶的密闭容器中,并定期更换碱溶液。在室温下孵育3.5个月;在此期间,将小瓶中的碱溶液更换并滴定12次。根据0.3 N NaOH溶液吸收的二氧化碳量绘制矿化曲线,并针对每个时间间隔进行计算;用闪烁法测定其 14 C含量。实验处理还包括确定使用重液或重液和0.1 N NaOH溶液预处理的AE层中材料中的OM矿化速率。揭示了在田间条件下相互作用7个月和20个月后,以葡萄糖,甘氨酸和尿嘧啶形式施用到土壤中的标记有机物矿化速率之间的差异。研究了用重液体和0.1 N NaOH溶液连续萃取不稳定有机物后矿化速率的变化。结果表明,在20个月的时间里,土壤中标记的低分子量有机化合物的转化包括将其强力地包含在腐殖质成分中,这可以通过天然和 14的矿化常数值相近的证实。 C标签的OM。此外,重液或重液和NaOH溶液处理对天然和 14 C标记的OM的矿化作用几乎相同。田间实验7个月后采集的样品中天然和 14 C标记的OM的矿化常数存在显着差异。注释来自Pochvovedenie(2012)12,1259-1268(Ru)。

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