Long term laboratory column experiments to simulate bank filtration: Factors controlling removal of sulfamethoxazole

2011 ◽  
Vol 45 (1) ◽  
pp. 211-220 ◽  
Author(s):  
Benno Baumgarten ◽  
Jeannette Jährig ◽  
Thorsten Reemtsma ◽  
Martin Jekel
2014 ◽  
Vol 48 ◽  
pp. 168-175 ◽  
Author(s):  
Vladislav Chrastný ◽  
Aleš Vaněk ◽  
Eva Čadková ◽  
Alice Růžičková ◽  
Ivana Galušková ◽  
...  

2021 ◽  
Author(s):  
Madiha Khadhraoui ◽  
John Molson ◽  
Najat Bhiry

<p>In natural porous environments, soil particle migration during flow plays an important role in soil stability and pollutant transport by affecting soil mechanical properties and water quality. In northern areas, permafrost degradation alters the subsurface connection pathways leading to mass movements and rearrangement of the soil. To date, few models have included the influence of temporal and spatial variations of flow velocity and porous media heterogeneity on the transport and deposition of suspended particles.</p><p>In this study, laboratory column experiments and a numerical model were used to investigate these issues. The laboratory column experiments were carried out under different flow rates and the effect of porous media heterogeneity was investigated using different grain size distributions. The soil columns were reconstituted from several samples taken in the studied site, the Tasiapik Valley, located in the discontinuous permafrost zone near Umiujaq, Nunavik, Québec. During the experiments, the spatio-temporal distribution of the porosity and the hydraulic conductivity was monitored using X-ray computed tomography imaging (CT-SCAN). Using the pore water velocity computed from the groundwater flow solution, the advection–dispersion transport equation with a first-order kinetic term for particle deposition was solved using the finite element model Heatflow/Smoker. The dependency of the attachment kinetics on the pore water velocity and on the porous media heterogeneity was included. The model was tested and validated with an analytical solution and calibrated with the experimental data. Our simulations highlight the roles of hydrodynamic conditions and soil characteristics on particle transport and deposition mechanisms and the susceptibility of the porous medium to thermo-suffosion in permafrost environments.</p>


2010 ◽  
Vol 213 (1-4) ◽  
pp. 437-458 ◽  
Author(s):  
Mariam Ouangrawa ◽  
Michel Aubertin ◽  
John W. Molson ◽  
Bruno Bussière ◽  
Gérald J. Zagury

2011 ◽  
Vol 47 (4) ◽  
Author(s):  
Jun Yin ◽  
Roy Haggerty ◽  
Deborah L. Stoliker ◽  
Douglas B. Kent ◽  
Jonathan D. Istok ◽  
...  

2002 ◽  
Vol 36 (22) ◽  
pp. 4818-4823 ◽  
Author(s):  
Robert Artinger ◽  
Wolfram Schuessler ◽  
Franz Scherbaum ◽  
Dieter Schild ◽  
Jae-Il Kim

2020 ◽  
Author(s):  
Márton Dencső ◽  
Szandra Baklanov ◽  
Ágota Horel ◽  
Györgyi Gelybó ◽  
Eszter Tóth

<p>This study focuses on the soil N<sub>2</sub>O emission of arable fields. We initially set up several soil column experiments in laboratory and based on these findings we started field measurements in a long term tillage experiment at Józsefmajor Experimental and Training Farm, Hungary. For the column experiments we collected undisturbed soil columns (d=10 cm, h=10 cm) from mouldboard ploughing (P) and no-till (NT) treatments.  We investigated the effect of different fertilizer doses (40, 80, 160, 240 kg h<sup>-1</sup> N), soil water content (SWC) and different tillage methods on soil N<sub>2</sub>O emission.</p><p>We found a nonlinear response of N<sub>2</sub>O emission on the applied fertilizer doses. The moderately fertilized (80-160 kg ha<sup>-1</sup> N) samples had the highest N<sub>2</sub>O emissions. Samples from NT had higher N<sub>2</sub>O emission than samples from P. We found better correlation between N<sub>2</sub>O emission and SWC in NT (R<sup>2</sup> is between 0.47 and 0.62) than in the P (R<sup>2</sup> is between 0.01 and 0.35).  The N<sub>2</sub>O emission values showed high spatial variability. The field measurements showed similar findings of N<sub>2</sub>O emission compared to the column experiments. In 2020 we intend to continue the field measurements and include further investigations of governing factors of soil N<sub>2</sub>O emission.</p>


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