Sulfamethazine and flubendazole in seepage water after the sprinkling of manured areas.
Pharmaceuticals are widely used in modern livestock production and can reach the environment via the application of manure containing excreted drugs. Limited information is available on the transport and fate of veterinary medicines applied to soils. Therefore, we assessed the potential for the sulphonamide antibiotic sulfamethazine (SMT) and the antiparasitic drug flubendazole (FLUB) including their metabolites to move from agricultural manure to drainage waters at 1m depth. A comparison was made of losses from sites under different land use (grassland versus arable cropping) as well as losses from neighbouring plots under the same land use. Liquid manure from pigs treated with SMT and FLUB was spread on 10 x 30 m2 plots (750l per plot). SMT concentration in slurry ranged from 600 to 1700 microg l(-1) (metabolite acetyl-SMT 280-1700 microg l(-1)) and FLUB concentration ranging from 25 to 56 microg l(-1) (metabolite amino-FLUB 32-110 microg l(-1), hydroxy-FLUB 19-38 microg l(-1)). About 1h after application heavy rainfall (50mm in 2.5h) was simulated by sprinkler irrigation. Drainage flow started within 1h after the commencement of sprinkling. SMT and FLUB concentrations in leachate reached values of up to 16 microg l(-1) and 0.3 microg l(-1), respectively. Loss rates (relative to the applied amounts) from the neighbouring sites under arable cropping ranged from 2.8% to 5.4% for SMT and 0.8% to 3.1% for FLUB (including metabolites). On the permanent grassland plot, due to its multitude of macropores, loss rates reached values up to 10% for SMT and 16% for FLUB (including metabolites). These results demonstrate that the variability in leaching of veterinary drugs may be high even between large neighbouring plots, depending on site heterogeneity and land use.
Bayerisches Landesamt für Umwelt, München, Germany. klaus.weiss@lfu.bayern.de
Klaus
K
Weiss
Walter
W
Schüssler
Michael
M
Porzelt
D000383:Agriculture; D000818:Animals; D000900:Anti-Bacterial Agents / Q000032:analysis*; D000969:Antinematodal Agents / Q000032:analysis*; D002853:Chromatography, Liquid; D004350:Drug Residues / Q000032:analysis*; D004553:Electric Conductivity; D008372:Manure / Q000032:analysis*; D013058:Mass Spectrometry; D008463:Mebendazole / Q000031:analogs & derivatives* / Q000032:analysis; D006109:Poaceae; D011891:Rain; D013418:Sulfamethazine / Q000032:analysis*; D013552:Swine; D014867:Water / Q000032:analysis*
D000900:Anti-Bacterial Agents; D000969:Antinematodal Agents; D008372:Manure; D014867:Water; D013418:Sulfamethazine; D008463:Mebendazole; C018945:flubendazole