Redistribution and persistence of microorganisms and steroid hormones after soil-injection of swine slurry
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Redistribution and persistence of microorganisms and steroid hormones after soil-injection of swine slurry. / Amin, Mostofa; Bech, Tina B.; Forslund, Anita; Hansen, Martin; Petersen, Søren O.; Lægdsmand, Mette.
I: The Science of the Total Environment, Bind 466-467, 2014, s. 1003-1010.Publikation: Bidrag til tidsskrift › Tidsskriftartikel › Forskning › fagfællebedømt
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TY - JOUR
T1 - Redistribution and persistence of microorganisms and steroid hormones after soil-injection of swine slurry
AU - Amin, Mostofa
AU - Bech, Tina B.
AU - Forslund, Anita
AU - Hansen, Martin
AU - Petersen, Søren O.
AU - Lægdsmand, Mette
N1 - © 2013.
PY - 2014
Y1 - 2014
N2 - The redistribution and fate of contaminants in pig slurry after direct injection were investigated at two field sites, Silstrup (sandy clay loam) and Estrup (sandy loam), in Denmark. Intact soil samples were collected for up to seven weeks after slurry injection and concentrations of Salmonella Typhimurium Bacteriophage 28B (phage 28B), Escherichia coli, steroid hormones and other slurry components (water, volatile solids, chloride and mineral N) determined in and around the injection slit. The two experiments at Silstrup and Estrup differed with respect to slurry solid content (6.3 vs. 0.8%), as well as soil clay content (27 vs. 15%) and differed considerably with respect to the initial redistribution of slurry-borne contaminants in soil. The transport of microorganisms from the slurry injection slit to the surrounding soil was much lower than that of mineral N and chloride due to attachment and entrapment. The redistribution of E. coli was more affected by site-specific conditions compared to phage 28B, possibly due to the larger cell size of E. coli. The overall recovery of phage 28B was 0.8-4%, and of E. coli 0.0-1.3% in different samples, by the end of the study. Nine different steroid hormones were detected in the slurry slit, and a slow redistribution to the surrounding soil was observed. Overall recovery of estrogens was 0.0 to 6.6% in different samples. The study showed that the combination of soil and slurry properties determined the initial spreading of contaminants, and hence the potential for subsequent leaching.
AB - The redistribution and fate of contaminants in pig slurry after direct injection were investigated at two field sites, Silstrup (sandy clay loam) and Estrup (sandy loam), in Denmark. Intact soil samples were collected for up to seven weeks after slurry injection and concentrations of Salmonella Typhimurium Bacteriophage 28B (phage 28B), Escherichia coli, steroid hormones and other slurry components (water, volatile solids, chloride and mineral N) determined in and around the injection slit. The two experiments at Silstrup and Estrup differed with respect to slurry solid content (6.3 vs. 0.8%), as well as soil clay content (27 vs. 15%) and differed considerably with respect to the initial redistribution of slurry-borne contaminants in soil. The transport of microorganisms from the slurry injection slit to the surrounding soil was much lower than that of mineral N and chloride due to attachment and entrapment. The redistribution of E. coli was more affected by site-specific conditions compared to phage 28B, possibly due to the larger cell size of E. coli. The overall recovery of phage 28B was 0.8-4%, and of E. coli 0.0-1.3% in different samples, by the end of the study. Nine different steroid hormones were detected in the slurry slit, and a slow redistribution to the surrounding soil was observed. Overall recovery of estrogens was 0.0 to 6.6% in different samples. The study showed that the combination of soil and slurry properties determined the initial spreading of contaminants, and hence the potential for subsequent leaching.
KW - Animals
KW - Colony Count, Microbial
KW - Denmark
KW - Escherichia coli
KW - Gas Chromatography-Mass Spectrometry
KW - Gonadal Steroid Hormones
KW - Manure
KW - Nitrogen
KW - Salmonella Phages
KW - Soil Microbiology
KW - Soil Pollutants
KW - Sus scrofa
KW - Tandem Mass Spectrometry
KW - water treatment
KW - aecal contaminati on
KW - heavy metals
KW - food hygiene
KW - waste- water nutrients value
U2 - 10.1016/j.scitotenv.2013.07.051
DO - 10.1016/j.scitotenv.2013.07.051
M3 - Journal article
C2 - 23994734
VL - 466-467
SP - 1003
EP - 1010
JO - Science of the Total Environment
JF - Science of the Total Environment
SN - 0048-9697
ER -
ID: 123674378