Transfer of Escherichia coli to water from drained and undrained grassland after grazing

被引:57
作者
Oliver, DM
Heathwaite, L [1 ]
Haygarth, PM
Clegg, CD
机构
[1] Univ Lancaster, Ctr Sustainable Water Management, Lancaster Environm Ctr, Lancaster LA1 4YQ, England
[2] Univ Sheffield, Dept Geog, Sheffield S10 2TN, S Yorkshire, England
[3] Inst Grassland & Environm Res, N Wyke Res Stn, Soil Sci & Environm Qual Team, Okehampton EX20 2SB, Devon, England
关键词
D O I
10.2134/jeq2004.0327
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The aim of this study was to determine the load of Escherichia coli transferred via drainage waters from drained and undrained pasture following a grazing period. Higher concentrations (ranging between 10(4) and 10(3) colony forming units [CFU] g(-1)) of E. coli persisted in soil for up to 60 d beyond the point where cattle were removed from the plots, but these eventually declined in the early months of spring to concentrations less than 10(2) CFU g(-1). The decline reflects the combined effect of cell depletion from the soil store through both wash-out and die-off of E. coli. No difference (P > 0.05) was observed in E. coli loads exported from drained and undrained plots. Similarly, no difference (P > 0.05) was observed in E. coli concentrations in drainage waters of mole drain flow and overland plus subsurface interflow. Intermittent periods of elevated discharge associated with storm events mobilized E. coli at higher concentrations (e.g., in excess of 400 CFU mL(-1)) than observed during low flow conditions (often < 25 CFU mL(-1)). The combination of high discharge and cell concentrations resulted in the export of E. coli loads from drained and undrained plots exceeding 10(6) CFU L-1 s(-1). The results highlight the potential for drained land to export E. coli loads comparable with those transferred from undrained pasture.
引用
收藏
页码:918 / 925
页数:8
相关论文
共 39 条
[1]  
Abu-Ashour J, 2000, ENVIRON TOXICOL, V15, P149, DOI 10.1002/(SICI)1522-7278(2000)15:2<149::AID-TOX11>3.3.CO
[2]  
2-F
[3]  
Abu-Ashour J, 1998, T ASAE, V41, P1043, DOI 10.13031/2013.17267
[4]   TRANSPORT OF MICROORGANISMS THROUGH SOIL [J].
ABUASHOUR, J ;
JOY, DM ;
LEE, H ;
WHITELEY, HR ;
ZELIN, S .
WATER AIR AND SOIL POLLUTION, 1994, 75 (1-2) :141-158
[5]   Leaching of bacterial indicators of faecal contamination through four New Zealand soils [J].
Aislabie, J ;
Smith, JJ ;
Fraser, R ;
McLeod, M .
AUSTRALIAN JOURNAL OF SOIL RESEARCH, 2001, 39 (06) :1397-1406
[6]   Impact of agricultural practices and river catchment characteristics on river and bathing water quality [J].
Aitken, MN .
WATER SCIENCE AND TECHNOLOGY, 2003, 48 (10) :217-224
[7]   HYDROLOGICAL CONSEQUENCES OF ARTIFICIAL-DRAINAGE OF GRASSLAND [J].
ARMSTRONG, AC ;
GARWOOD, EA .
HYDROLOGICAL PROCESSES, 1991, 5 (02) :157-174
[8]  
AVERY BW, 1980, SOIL SURVEY ENGLAND
[9]  
European Economic Community, 1979, Official Journal L, V145, P1, DOI [10.1039/AP9842100196, DOI 10.1039/AP9842100196]
[10]   FACTORS AFFECTING CONCENTRATION OF FECAL BACTERIA IN LAND-DRAINAGE WATER [J].
EVANS, MR ;
OWENS, JD .
JOURNAL OF GENERAL MICROBIOLOGY, 1972, 71 (AUG) :477-&