PL EN


Preferencje help
Widoczny [Schowaj] Abstrakt
Liczba wyników
2014 | 28 | 1 |

Tytuł artykułu

Influence of soil tillage and erosion on the dispersion of glyphosate and aminomethylphosphonic acid in agricultural soils

Treść / Zawartość

Warianty tytułu

Języki publikacji

EN

Abstrakty

EN
Erosion processes can strongly influence the dissipation of glyphosate and aminomethylphosphonic acid applied with Roundup Max in agricultural soils; in addition, the soil structure state shortly before erosive precipitations fall can be a key parameter for the distribution of glyphosate and its metabolite. Field rain simulation experiments showed that severe erosion processes immediately after application of Roundup Max can lead to serious unexpected glyphosate loss even in soils with a high presumed adsorption like the Cambisols, if their structure is unfavourable. In one of the no-tillage-plot of the Cambisol, up to 47% of the applied glyphosate amount was dissipated with surface run-off. Moreover, at the Chernozem site with high erosion risk and lower adsorption potential, glyphosate could be found in collected percolation water transported far outside the 2x2 m experimental plots. Traces of glyphosate were found also outside the treated agricultural fields.

Wydawca

-

Rocznik

Tom

28

Numer

1

Opis fizyczny

p.93-100,fig.,ref.

Twórcy

  • Department of Forest and Soil Sciences, University of Natural Resources and Life Sciences in Vienna, Vienna, Peter-Jordan-Strasse 82, 1190 Vienna, Austria
autor
  • Department of Forest and Soil Sciences, University of Natural Resources and Life Sciences in Vienna, Vienna, Peter-Jordan-Strasse 82, 1190 Vienna, Austria
autor
  • Department of Forest and Soil Sciences, University of Natural Resources and Life Sciences in Vienna, Vienna, Peter-Jordan-Strasse 82, 1190 Vienna, Austria
  • Department of Forest and Soil Sciences, University of Natural Resources and Life Sciences in Vienna, Vienna, Peter-Jordan-Strasse 82, 1190 Vienna, Austria
autor
  • Federal Agency for Water Management, Institute for Land and Water Management Research, Pollnstrasse 1, 3252 Petzenkirchen, Austria
autor
  • Federal Agency for Water Management, Institute for Land and Water Management Research, Pollnstrasse 1, 3252 Petzenkirchen, Austria

Bibliografia

  • Aparicio V.C., De Geronimo E., Marino D., Primost J., Carriquiriborde P., and Costa J.L., 2013. Environmental fate of glyphosate and aminomethylphosphonic acid in surface waters and soil of agricultural basins. Chemosphere, 93, 1866-1873.
  • Borggaard O.K. and Gimsing A.L., 2008. Fate of glyphosate in soil and the possibility of leaching to ground and surface waters: A review. Pest Manag. Sci., 64, 441-456.
  • Candela L., Álvarez-Benedi J., Condesso de Melo M.T., and Rao P.S.C., 2007. Laboratory studies on glyphosate transport in soils of the Maresme area near Barcelona, Spain: Transport model parameter estimation. Geoderma, 140, 8-16.
  • Cerdeira A.L. and Duke S.O., 2006. The current status and environmental impacts of glyphosate-resistant crops: A review. J. Environ. Quality, 35, 1633-1658.
  • Christoffoleti P.J., Galli A.J.B., Carvahlo S.J.P., Moreira M.S., NicolaiM., Foloni L.L., Martins B.A.B., and Ribeiro D.N., 2008. Glyphosate sustainability in South American cropping systems. Pest Manag. Sci., 64, 422-427.
  • Degenhardt D., Humphries D., Cessna A.J.,Messing P., Badiou, P.H., Raina R., Farenhorst A., and Pennock D.J., 2012. Dissipation of glyphosate and aminomethylphosphonic acid in water and sediment of two Canadian prairie wetlands. J. Environ. Sci., Pesticides, Food Contaminants, Agric. Waste, 47, 631-639.
  • De Jonge H., De Jonge L.W., and Jacobsen O.H., 2000. [14C] glyphosate transport in undisturbed topsoil columns. Pest Manag. Sci., 56, 909-915.
  • Donald D.B.,Hunter F.G., SverkoE., Hill B.D., and Syrgiannis J., 2005.Mobilization of pesticides on an agricultural landscape flooded by a torrential storm. Environ. Toxicol. Chem., 24, 2-10.
  • Eberbach P., 1997. Applying non-steady-state compartmental analysis to investigate the simultaneous degradation of soluble and sorbed glyphosate (N-(Phosphonomethyl)glycine) in four soils. Pestic. Sci., 52, 229-240.
  • Ghanem A., Bados P., Estaun A.R., de Alencastro L.F., Taibi S., Einhorn J., and Mougin C., 2007. Concentrations and specific loads of glyphosate, diuron, atrazin, nonylphenol and metabolites thereof in French urban sewage sludge. Chemosphere, 69, 1368-1373.
  • Giesy J.P., Dobson S., and Solomon K.R., 2000. Ecotoxicological risk assessment for Roundup herbicide. Reviews Environ. Contamination Toxicol., 167, 35-120.
  • Gimsing A.L. and Borggaard O.K., 2002. Competitive adsorption and desorption of glyphosate and phosphate on clay silicates and oxides. Clay Minerals, 37, 509-515.
  • Gimsing A.L., Borggaard O.K., Jacobsen O.S., AamandJ., and Sorensen J., 2004. Chemical and microbiological soil characteristics controlling glyphosate mineralization in Danish surface soils. Appl. Soil Ecol., 27, 233-242.
  • Gjettermann B., Petersen C.T., Hansen S., Bender Koch C., and Stycze M., 2011. Kinetics of glyphosate desorption from mobilized soil particles. Soil Sci. Soc. Am. J., 75, 434-443.
  • Gjetterman B., Petersen C.T., Koch C.B., Spliid N.H., Grön C., and Baun D.L., 2009. Particle-facilitated pesticide leaching from differently structured soil monoliths. J. Environ. Quality, 38, 2382-2393.
  • Landry D., Dousset S., Fournier J.-C., and Andreux F., 2005. Leaching of glyphosate and AMPA under two soil management practices in Burgundy vineyards (Vosne-Romanée, 21-France). Environ. Pollut., 138, 191-200.
  • Locke M.A. and Bryson C.T., 1997. Herbicide-soil interactions in reduced tillage and plant residue management systems. Weed Sci., 45, 307-320.
  • Locke M.A., Zablotowics R.M., and Reddy K.N., 2008. Integrating soil conservation practices and glyphosate-resistant crops: Impacts on soil. Pest Manag. Sci., 64, 457-469.
  • Mamy L., Barriuso E., and Gabrielle B., 2005. Environmental fate of herbicides trifularin, metazachlor, metamitron and sulcotrione compared with that of glyphosate, a substitute broad spectrum herbicide for different glyphosate-resistant crops. Pest. Manag. Sci., 61, 905-916.
  • Peruzzo P.J., Porta A.A., and Ronco A.E., 2008. Levels of glyphosate in surface waters, sediments and soils associated with direct sowing soybean cultivation in north pampasic region of Argentina. Environ. Pollut., 156(1), 61-66.
  • Pessagno R.C., Torres Sánchez R.M, and dos Santos Afonso M., 2008. Glyphosate behavior at soil and mineral-water interferences. Environ. Pollut., 153(1), 53-59.
  • Rampazzo N., Rampazzo Todorovic G., Mentler A., and Blum W.E.H., 2013. Adsorption of glyphosate andAMPAin agricultural Austrian soils. Int. Agrophys., 27, 203-209.
  • Rueppel M.L., Brightwell B.B., Schaefer J., and Marvel J.T., 1977. Metabolism and degradation of glyphosate in soil and water. J. Agric. Food Chem., 25(3), 517-528.
  • Siimes K., Rämo S., Welling L., Nikunen U., and Laitinen P., 2006. Comparison of the behavior of three herbicides in a field experiment under bare soil conditions. Agric.Water Manag., 84, 53-64.
  • Soulas G. and Lagacherie B., 2001. Modelling of microbial degradation of pesticides in soils. Biol. Fertil. Soils, 33, 551-557.
  • Strauss P., Pitty J., Pfeffer M., and Mentler A., 2000. Rainfall Simulation for outdoor Experiments. In: Current Research Methods to Assess the Environmental Fate of Pesticides (Eds P. Jamet, J. Coirnejo), INRA Press, Avignon, France. Vereecken H., 2005. Mobility and leaching of glyphosate: A review. Pest Manag. Sci., 61, 1139-1151.
  • WRB, 2006. World reference base for soil resources 2006. Reports, 103, FAO Press, Rome, Italy.
  • Zaranyika M.F. and Nyandro M.G., 1993. Degradation of glyphosate in the aquatic environment: An enzymatic kinetic model that takes into account microbial degradation of both free and colloidal (or sediment) particle adsorbed glyphosate. J. Agric. Food Chem., 41, 838-842.

Typ dokumentu

Bibliografia

Identyfikatory

Identyfikator YADDA

bwmeta1.element.agro-d501c38b-c87b-4bd7-a6f8-14eb0e10629d
JavaScript jest wyłączony w Twojej przeglądarce internetowej. Włącz go, a następnie odśwież stronę, aby móc w pełni z niej korzystać.