scholarly journals Runoff event characteristics - Supporting Information for Winter et al. (2022)

Keyword(s):  
Hydrobiologia ◽  
2004 ◽  
Vol 517 (1-3) ◽  
pp. 171-177
Author(s):  
Steven W. Effler ◽  
David M. O'Donnell ◽  
MaryGail Perkins ◽  
David G. Smith

2019 ◽  
Vol 48 (4) ◽  
pp. 841-849 ◽  
Author(s):  
Henry F. Wilson ◽  
Nora J. Casson ◽  
Aaron J. Glenn ◽  
Pascal Badiou ◽  
Lyle Boychuk

Chemosphere ◽  
2012 ◽  
Vol 87 (7) ◽  
pp. 684-691 ◽  
Author(s):  
Richard E. Lizotte ◽  
F. Douglas Shields ◽  
Justin N. Murdock ◽  
Scott S. Knight

2009 ◽  
Vol 23 (14) ◽  
pp. 2095-2101 ◽  
Author(s):  
Steve W. Lyon ◽  
Sharon L. E. Desilets ◽  
Peter A. Troch

2013 ◽  
Vol 42 (4) ◽  
pp. 462-471 ◽  
Author(s):  
Laura Palleiro ◽  
María Luz Rodríguez-Blanco ◽  
María Mercedes Taboada-Castro ◽  
María Teresa Taboada-Castro

2020 ◽  
Author(s):  
Rafael Muñoz-Carpena ◽  
Stefan Reichenberger ◽  
Robin Sur

<p>Vegetative filter strips (VFS) are commonly implemented in the field to mitigate runoff pesticide inputs into surface waters and protect aquatic ecosystems. The efficiency of this mitigation practice can be evaluated within the current regulatory high-tier, long-term environmental risk assessments (ERA) in combination with VFSMOD, an established and commonly used numerical model for the analysis of runoff, sediment, and pesticide transport in VFS. For every rainfall/runoff event in the long-term time series, VFSMOD takes the PRZM calculated edge-of-the-field surface runoff, eroded sediment yield, and dissolved and particle-bound pesticide load.  It then calculates infiltration, sedimentation and pesticide trapping in the VFS during the event, and the outflow into the downslope aquatic body for further calculations and risk analysis. Importantly, at the end of each event, VFSMOD calculates the amount of pesticide residue retained in the filter (sediment-bound and infiltrated in the liquid phase), its degradation until the next event in the series, and the fraction of pesticide residue that is remobilized and added to the next runoff event. In earlier VFSMOD versions, full remobilization of the pesticide residue sorbed to sediment and that dissolved in the soil surface mixing layer (typically the top 0.5-5 cm) was calculated conservatively. Recent VFSMOD ERA applications for very highly-sorbed (i.e. pyrethroids) or persistent pesticides indicate that the full remobilization scheme might be too conservative in some cases. In this work, we evaluate new alternative partial remobilization schemes in VFSMOD, i.e. no remobilization of adsorbed residues, but full remobilization of dissolved residues in the mixing layer, or alternatively just a fraction of the mixing layer by diffusive exchange with the runoff. We evaluate the effects of the alternative remobilization schemes on observed total VFS pesticide reductions from available field data. In addition, employing global sensitivity analysis, we assess the relative importance of the alternative remobilization model structures in the context of the expected field variability of other known drivers of VFS efficiency (hydrology, soils, vegetation, pesticide chemical characteristics). The study provides science-based recommendations for future high-tier pesticide ERA with VFS mitigation.</p>


2004 ◽  
Vol 49 (3) ◽  
pp. 117-123 ◽  
Author(s):  
C.M. Cooper ◽  
M.T. Moore ◽  
E.R. Bennett ◽  
S. Smith ◽  
J.L. Farris ◽  
...  

Vegetated agricultural ditches play an important role in mitigation of pesticides following irrigation and storm runoff events. In a simulated runoff event in the Mississippi (USA) Delta, the mitigation capacity of a drainage ditch using the pyrethroid esfenvalerate (Asana XLTM) was evaluated. The pesticide was amended to soil prior to the runoff event to simulate actual runoff, ensuring the presence of esfenvalerate in both water and suspended particulate phases. Water, sediment, and plant samples were collected temporally and spatially along the drainage ditch. Even with mixing of the pesticide with soil before application, approximately 99% of measured esfenvalerate was associated with ditch vegetation (Ludwigia peploides, Polygonum amphibium, and Leersia oryzoides) three hours following event initiation. This trend continued for the 112 d study duration. Simple modeling results also suggest that aqueous concentrations of esfenvalerate could be mitigated to 0.1% of the initial exposure concentration within 510 m of a vegetated ditch. Observed field half-lives in water, sediment, and plant were 0.12 d, 9 d, and 1.3 d, respectively. These results validate the role vegetation plays in the mitigation of pesticides, and that ditches are an indispensable component of the agricultural production landscape.


2015 ◽  
Vol 30 (9) ◽  
pp. 1449-1466 ◽  
Author(s):  
G. Zuecco ◽  
D. Penna ◽  
M. Borga ◽  
H. J. van Meerveld

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