Effect of different organic amendments on the dissipation of linuron, diazinon and myclobutanil in an agricultural soil incubated for different time periods.
Dissipation kinetics of pesticides belonging to three chemical groups (linuron, diazinon and myclobutanil) was studied in an unamended agricultural soil and in this soil amended with three organic residues: sewage sludge (SS), grape marc (GM) and spent mushroom substrate (SMS). The soils were incubated with the residues outdoors for one and 12 months. Mineralized, extracted and non-extractable fractions were also studied for (14)C-linuron and (14)C-diazinon. The dissipation kinetics was fitted to single first-order or first-order multicompartment models. The dissipation rate (k) decreased in the order diazinon>linuron>myclobutanil, and DT50 values decreased for linuron (1.6-4.8 times) or increased for myclobutanil (1.7-2.6 times) and diazinon (1.8-2.3 times) in the amended soils relative to the unamended soil. The lowest DT50 values for the three pesticides were recorded in GM-amended soil, and the highest values in SMS-amended soil. After 12 months of soil incubation, DT50 values decreased in both the unamended and amended soils for linuron, but increased for the unamended and SMS-amended soil for diazinon and myclobutanil. A certain relationship was observed between the sorption of pesticides by the soils and DT50 values, although it was significant only for myclobutanil (p<0.05). Dissipation mechanism recorded the lowest mineralization of (14)C-pesticides in the GM-soil despite the highest dissipation rate in this soil. The extracted (14)C-residues decreased with incubation time, with increased formation of non-extractable residues, higher in amended soils relative to the unamended soil. Soil dehydrogenase activity was, in general, stimulated by the addition of the organic amendments and pesticides to the soil after one month and 12 months of incubation. The results obtained revealed that the simultaneous use of amendments and pesticides in soils requires a previous study in order to check the environmental specific persistence of these compounds and their effectiveness in amended soils.
Institute of Natural Resources and Agrobiology of Salamanca (IRNASA-CSIC), 40-52 Cordel de Merinas, 37008 Salamanca, Spain.
Jesús M
JM
Marín-Benito
Institute of Natural Resources and Agrobiology of Salamanca (IRNASA-CSIC), 40-52 Cordel de Merinas, 37008 Salamanca, Spain.
Eliseo
E
Herrero-Hernández
Department of Agriculture and Food, University of La Rioja, 51 Madre de Dios, 26006 Logroño, Spain.
M Soledad
MS
Andrades
Institute of Natural Resources and Agrobiology of Salamanca (IRNASA-CSIC), 40-52 Cordel de Merinas, 37008 Salamanca, Spain. Electronic address: mjesus.sanchez@irnasa.csic.es.
María J
MJ
Sánchez-Martín
Institute of Natural Resources and Agrobiology of Salamanca (IRNASA-CSIC), 40-52 Cordel de Merinas, 37008 Salamanca, Spain.
M Sonia
MS
Rodríguez-Cruz
D000363:Agaricales; D000383:Agriculture; D003976:Diazinon / Q000737:chemistry; D008044:Linuron / Q000737:chemistry; D008956:Models, Chemical; D009570:Nitriles / Q000737:chemistry; D010575:Pesticides / Q000737:chemistry*; D012722:Sewage; D012987:Soil / Q000737:chemistry*; D012989:Soil Pollutants / Q000737:chemistry*; D014230:Triazoles / Q000737:chemistry
D009570:Nitriles; D010575:Pesticides; D012722:Sewage; D012987:Soil; D012989:Soil Pollutants; D014230:Triazoles; D008044:Linuron; C446685:systhane; D003976:Diazinon
Agricultural soil; Dissipation; Mineralization; Organic amendment; Pesticide; Soil activity