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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{sub}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{sub}(il)), active inorganic P (P{sub}(ia)), stable inorganic P (P{sub}(is)), fresh organic P (P{sub}(of)), and more stable organic P ({sub}(oh))- The major model modifications made were: (1) initialization of P{sub}(il) from the Finnish soil test results (ammonium acetate extractable P, P{sub}(AAC))> (2) initialization of P{sub}(ia) and P{sub}(is) from P{sub}(il), assuming equilibrium; (3) revision of the P availability factor (F{sub}l), which regulates the flow between P{sub}(il) and P{sub}(ia); and (4) calculation of the initial values of P{sub}(oh) from soil organic carbon content. These modifications aimed to improve simulation of P{sub}(il) on the basis of data obtained from soil testing. Proper simulation of changes in P{sub}(il), reflected by the soil test P (P{sub}(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{sub}(AAC) at annual P application rates of 0 and 30 kg ha{sup}(-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{sup}(-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状态的变化和影响土壤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 {sub} 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 {sub}(il)),活性无机P(P {sub}(ia)),稳定的无机P(P {sub}(is)),新鲜有机P(P {sub }(of))和更稳定的有机P({sub}(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)初始化P {sub}(il) ,P {sub}(AAC))>(2)初始化P {sub}(ia)和P {sub}(is)来自P {sub}(il),假定为平衡; (3)修订P可用性因子(F {sub} l),以调节P {sub}(il)和P {sub}(ia)之间的流量; (4)根据土壤有机碳含量计算P {sub}(oh)的初始值。这些修改旨在根据从土壤测试中获得的数据来改善对P {sub}(il)的仿真。正确模拟土壤测试P(P {sub}(AAC))反映的P {sub}(il)变化非常重要,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作物中P {sub}(AAC)在0和30 kg ha {sup}(-1)的年施磷量下的变化,但不能完全应付大量盈余。每年60 kg P ha {sup}(-1)所产生的磷含量。

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