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SIMULATING PROCESSES OF SOIL PHOSPHORUS IN GEOLOGICALLY YOUNG ACIDIC SOILS OF FINLAND

机译:芬兰地质年轻酸土中土壤磷的模拟过程

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To properly simulate phosphorus (P) loading from agricultural land to waters, changes in soil P status and processes affecting soil P have to be described adequately. For practical reasons, a model has to rely on data that are commonly available. In this study, the P submodel of the ICECREAM model, based on the CREAMS, GLEAMS, and EPIC models, was adapted to simulate young acidic soils, which prevail in Finland. These soils have a high P sorption capacity, plenty of inorganic P in a non-reactive apatitic form, and the organic matter content (O r ) in the plow layer is commonly about 5%. The model was modified mainly on the basis of 12 long-term fertilization experiments and tested on three other soils. The P pools considered were labile P (P il ), active inorganic P (P ia ), stable inorganic P (P is ), fresh organic P (P of ), and more stable organic P (P oh ). The major model modifications made were: (1) initialization of P il from the Finnish soil test results (ammonium acetate extractable P, P AAc ); (2) initialization of P ia and P is from P il , assuming equilibrium; (3) revision of the P availability factor (F l ), which regulates the flow between P il and P ia ; and (4) calculation of the initial values of P oh from soil organic carbon content. These modifications aimed to improve simulation of P il on the basis of data obtained from soil testing. Proper simulation of changes in P il , reflected by the soil test P (P AAc ), is critical since it regulates the level of dissolved P in runoff water. After the modifications, the model was able to predict changes in P AAc at annual P application rates of 0 and 30 kg ha -1 in cereal cropping, but could not fully cope with a large surplus of P resulting from an annual rate of 60 kg P ha -1
机译:为了正确模拟从农田到水域的磷(P)含量,必须充分描述土壤P状况的变化和影响土壤P的过程。出于实际原因,模型必须依赖于通常可用的数据。在这项研究中,基于CREAMS,GLEAMS和EPIC模型的ICECREAM模型的P子模型适用于模拟在芬兰盛行的年轻酸性土壤。这些土壤具有高的P吸附能力,大量非反应性磷化形式的无机P,耕层中的有机物含量(O r )通常约为5%。该模型主要在12个长期施肥实验的基础上进行了修改,并在其他三种土壤上进行了测试。所考虑的P库为不稳定的P(P il ),活性无机P(P ia ),稳定的无机P(P is ),新鲜有机P(P of )和更稳定的有机P(P oh )。进行的主要模型修改是:(1)根据芬兰土壤测试结果(醋酸铵可萃取P,P AAc )初始化P il ; (2)P ia 和P 的初始化是从P il 假设平衡的。 (3)修改P可用性因子(F l ),以调节P il 和P ia 之间的流量; (4)根据土壤有机碳含量计算P oh 的初始值。这些修改旨在根据从土壤测试获得的数据来改进P il 的模拟​​。正确模拟土壤测试P(P AAc )反映的P il 的变化至关重要,因为它可以调节径流水中溶解的P的水平。修改后,该模型能够预测谷物种植中P AAc 在年P施用量为0和30 kg ha -1 时的变化,但无法完全应对每年60 kg P ha -1 导致大量的P过剩

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