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Transport and reduction of nitrate in clayey till underneath forest and arable land

机译:黏土中硝酸盐的运输和还原直至森林和耕地

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Transport and reduction of nitrate in a typically macroporous clayey till were examined at variable flow rate and nitrate flux. The experiments were carried out using saturated, large diameter (0.5 m), undisturbed soil columns (LUC), from a forest and nearby agricultural sites. Transport of nitrate was controlled by flow along the macropores (fractures and biopores) in the columns. Nitrate reduction (denitrification) determined under active flow mainly followed first order reactions with half-lives (t_(1/2)) increasing with depth (1.5-3.5 m) from 7 to 35 days at the forest site and 1-7 h at the agricultural site. Nitrate reduction was likely due to microbial degradation of accumulated organic matter coupled with successive consumption of O_2 and NO_3~- in the macropore water followed by reductive dissolution of Fe and Mn from minerals along the macropores. Concentrations of total organic carbon measured in soil samples were near identical at the two study sites and consequently not useful as indicator for the observed differences in nitrate reduction. Instead the high reduction rates at the agricultural site were positively correlated with elevated concentration of water-soluble organic carbon and nitrate-removing bacteria relative to the forest site. After high concentrations of water-soluble organic carbon in the columns from the agricultural site were leached they lost their elevated reduction rates, which, however, was successfully re-established by infiltration of new reactive organics represented by pesticides. Simulations using a calibrated discrete fracture matrix diffusion (DFMD) model could reasonably reproduce the denitrification and resulting flux of nitrate observed during variable flow rate from the columns.
机译:在可变的流速和硝酸盐通量下,对典型的大孔黏土中硝酸盐的运输和还原进行了研究。实验是使用来自森林和附近农业地点的饱和,大直径(0.5 m),原状土壤柱(LUC)进行的。硝酸盐的运输是通过沿色谱柱中大孔(裂缝和生物孔)的流动来控制的。在有效流量下测定的硝酸盐减少(反硝化作用)主要发生在一级反应之后,其中半衰期(t_(1/2))随着深度(1.5-3.5 m)的增加在林地从7天增加到35天,在林地增加1-7小时。农业现场。硝酸盐的减少很可能是由于累积的有机物的微生物降解,再加上大孔水中连续消耗O_2和NO_3〜-,然后还原铁和锰沿大孔中矿物质的溶解。在两个研究地点,土壤样品中测得的总有机碳浓度几乎相同,因此不能用作观察到的硝酸盐还原差异的指标。相反,相对于森林地点,农业地点的高减少率与水溶性有机碳和去除硝酸盐细菌的浓度升高呈正相关。从农业基地的柱子中滤出高浓度的水溶性有机碳后,它们失去了提高的还原速率,但是,通过渗透以农药为代表的新型反应性有机物成功地重新建立了还原速率。使用校准的离散断裂矩阵扩散(DFMD)模型进行的模拟可以合理地重现从色谱柱以可变流速观察到的反硝化作用和所产生的硝酸盐通量。

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