Department of Soil Amelioration, Faculty of Agriculture, University of Zagreb, Svetošimunska 25, 10000 Zagreb, Croatia; Université d'Orléans, ISTO, UMR 7327, 45071 Orléans, France; CNRS/INSU, ISTO, UMR 7327, 45071 Orléans, France; BRGM, ISTO, UMR 7327, BP 36009, 45060 Orléans, France; INRA, AgroParisTech, UMR 1091 EGC, F-78850 Thiverval-Grignon, France.
Université d'Orléans, ISTO, UMR 7327, 45071 Orléans, France; CNRS/INSU, ISTO, UMR 7327, 45071 Orléans, France; BRGM, ISTO, UMR 7327, BP 36009, 45060 Orléans, France.
Sci Total Environ. 2014 Nov 15;499:546-59. doi: 10.1016/j.scitotenv.2014.06.010. Epub 2014 Jun 21.
Transport processes in soils are strongly affected by heterogeneity of soil hydraulic properties. Tillage practices and compost amendments can modify soil structure and create heterogeneity at the local scale within agricultural fields. The long-term field experiment QualiAgro (INRA-Veolia partnership 1998-2013) explores the impact of heterogeneity in soil structure created by tillage practices and compost application on transport processes. A modeling study was performed to evaluate how the presence of heterogeneity due to soil tillage and compost application affects water flow and pesticide dynamics in soil during a long-term period. The study was done on a plot receiving a co-compost of green wastes and sewage sludge (SGW) applied once every 2 years since 1998. The plot was cultivated with a biannual rotation of winter wheat-maize (except 1 year of barley) and a four-furrow moldboard plow was used for tillage. In each plot, wick lysimeter outflow and TDR probe data were collected at different depths from 2004, while tensiometer measurements were also conducted during 2007/2008. Isoproturon concentration was measured in lysimeter outflow since 2004. Detailed profile description was used to locate different soil structures in the profile, which was then implemented in the HYDRUS-2D model. Four zones were identified in the plowed layer: compacted clods with no visible macropores (Δ), non-compacted soil with visible macroporosity (Γ), interfurrows created by moldboard plowing containing crop residues and applied compost (IF), and the plow pan (PP) created by plowing repeatedly to the same depth. Isoproturon retention and degradation parameters were estimated from laboratory batch sorption and incubation experiments, respectively, for each structure independently. Water retention parameters were estimated from pressure plate laboratory measurements and hydraulic conductivity parameters were obtained from field tension infiltrometer experiments. Soil hydraulic properties were optimized on one calibration year (2007/08) using pressure head, water content and lysimeter outflow data, and then tested on the whole 2004/2010 period. Lysimeter outflow and water content dynamics in the soil profile were correctly described for the whole period (model efficiency coefficient: 0.99) after some correction of LAI estimates for wheat (2005/06) and barley (2006/07). Using laboratory-measured degradation rates and assuming degradation only in the liquid phase caused large overestimation of simulated isoproturon losses in lysimeter outflow. A proper order of magnitude of isoproturon losses was obtained after considering that degradation occurred in solid (sorbed) phase at a rate 75% of that in liquid phase. Isoproturon concentrations were found to be highly sensitive to degradation rates. Neither the laboratory-measured isoproturon fate parameters nor the independently-derived soil hydraulic parameters could describe the actual multiannual field dynamics of water and isoproturon without calibration. However, once calibrated on a limited period of time (9 months), HYDRUS-2D was able to simulate the whole 6-year time series with good accuracy.
土壤中的输运过程受土壤水力性质的异质性强烈影响。耕作实践和堆肥改良可以改变土壤结构,并在农业用地的局部范围内产生异质性。长期野外实验 QualiAgro(INRA-Veolia 合作 1998-2013 年)探索了耕作实践和堆肥应用引起的土壤结构异质性对土壤中输运过程的影响。进行了一项建模研究,以评估由于土壤耕作和堆肥应用引起的异质性在长期内如何影响土壤中的水流和农药动态。该研究在一个自 1998 年以来每两年接受一次绿肥和污水污泥共堆肥(SGW)的地块上进行。该地块采用冬小麦-玉米的两年轮作(除了一年的大麦),并使用四沟犁板犁进行耕作。在每个地块中,从 2004 年开始,在不同深度收集了渗滤计流出物和 TDR 探头数据,同时在 2007/2008 年期间还进行了张力计测量。自 2004 年以来,在渗滤计流出物中测量了异噁草酮浓度。详细的剖面描述用于在剖面中定位不同的土壤结构,然后将其实施到 HYDRUS-2D 模型中。在犁耕层中确定了四个区域:没有可见大孔的压实土块(Δ)、没有可见大孔的非压实土壤(Γ)、由犁板犁耕形成的含有作物残茬和施用堆肥的沟间(IF)以及反复犁耕到同一深度的犁底(PP)。异噁草酮保留和降解参数分别通过实验室批量吸附和培养实验进行估计,每个结构分别进行估计。水分保持参数通过压力板实验室测量进行估计,水力传导率参数通过田间张力入渗计实验获得。使用压力头、含水量和渗滤计流出物数据对一个校准年(2007/08 年)进行了土壤水力性质的优化,然后在整个 2004/2010 年期间进行了测试。对整个时期(模型效率系数:0.99)进行了一些修正,以修正冬小麦(2005/06 年)和大麦(2006/07 年)的 LAI 估计值,以正确描述土壤剖面中的渗滤计流出物和含水量动态。使用实验室测量的降解率,并假设仅在液相中发生降解,会导致模拟异噁草酮在渗滤计流出物中的损失过大。在考虑到降解发生在固相(吸附)中,速率为液相中降解速率的 75%后,获得了异噁草酮损失的适当数量级。异噁草酮浓度对降解速率非常敏感。未经校准,既无法使用实验室测量的异噁草酮命运参数,也无法使用独立推导的土壤水力参数来描述实际的多年田间水和异噁草酮动态。然而,一旦在有限的时间(9 个月)内进行校准,HYDRUS-2D 就能够很好地准确模拟整个 6 年时间序列。