Faecal-indicator concentrations in waters draining lowland pastoral catchments in the UK: relationships with land use and farming practices.

Faecal-indicator budget studies have shown marine bathing water quality at two small UK coastal resorts, Staithes and Newport, to be adversely affected by riverine inputs from lowland pastoral catchments (J. Chartered Inst. Water Environ. Mangt. 12 (1998) 414). The present paper reports on presumptive coliform (PC), presumptive Escherichia coli (PE) and presumptive streptococci (PS) concentrations at 43 sampling points on watercourses within these catchments, and on their relationship with land use and livestock-related management practices, such as grazing and slurry/manure applications. The results show > 10-fold elevations in geometric mean faecal-indicator concentrations under high-flow conditions, compared with low flow, with maximum high-flow geometric mean PC, PE and PS concentrations of 2.6 x 10(6), 1.8 x 10(6) and 4.4 x 10(5) cfu/100 ml, respectively. High-flow geometric mean concentrations exhibit highly significant positive correlations with land use/management variables associated with intensive livestock farming, both within the individual catchments and in the two combined. Additional factors, such as antecedent weather conditions and topography, contribute to inter-catchment variability in water quality. Although inputs from diffuse and point sources of pollution were not quantified, point sources (e.g. runoff from farm yards) seem likely to be significant. The findings suggest that it may be possible to develop generic statistical models to predict microbial water quality from land use and farm management data. They also provide indirect evidence that channel bed sediment 'stores' closely reflect land use within their catchments and that there is little die-off of organisms along watercourses.

[1]  K. Jones,et al.  Distribution and seasonality of microbial indicators and thermophilic campylobacters in two freshwater bathing sites on the River Lune in northwest England , 1999, Journal of applied microbiology.

[2]  D Kay,et al.  Generation of fecal and total coliform surges by stream flow manipulation in the absence of normal hydrometeorological stimuli , 1982, Applied and environmental microbiology.

[3]  K. Jones,et al.  Campylobacters and Faecal Indicators in Streams and Rivers Subject to Farm Run-Off , 1996 .

[4]  K. Jones,et al.  Non‐compliance of beaches with the EU directives of bathing water quality: evidence of non‐point sources of pollution in Morecambe Bay , 1998, Journal of applied microbiology.

[5]  E. Geldreich,et al.  Seasonal Variations in Survival of Indicator Bacteria in Soil and Their Contribution to Storm-water Pollution. , 1967, Applied microbiology.

[6]  J. Ketley,et al.  Campylobacters, Helicobacters, and Related Organisms , 1996, Springer US.

[7]  J. Fleisher,et al.  Obtaining precise estimates in coliform enumeration , 1980 .

[8]  J. Crowther,et al.  Faecal‐Indicator Budgets for Recreational Coastal Waters: A Catchment Approach , 1998 .

[9]  D. Kay,et al.  Faecal indicator impacts on recreational waters: budget studies and diffuse source modelling , 1998, Journal of applied microbiology.

[10]  C. Hunter,et al.  The Occurrence of Coliform Bacteria in the Surface Soils of Two Catchment Areas in the Yorkshire Dales , 1991 .

[11]  K. Beven,et al.  INPUT OF FECAL COLIFORM BACTERIA TO AN UPLAND STREAM CHANNEL IN THE YORKSHIRE DALES , 1992 .

[12]  Desmond E. Walling,et al.  Water quality :processes and policy , 1999 .

[13]  J. Doran,et al.  Bacteriological Quality of Runoff Water from Pastureland , 1979, Applied and environmental microbiology.

[14]  C. Hunter,et al.  Agricultural land-use effects on the indicator bacterial quality of an upland stream in the Derbyshire peak district in the U.K. , 1999 .

[15]  Adrian McDonald,et al.  Reduction of coliform bacteria in two upland reservoirs: The significance of distance decay relationships , 1980 .

[16]  D. Kay,et al.  Non-outfall sources of faecal indicator organisms affecting the compliance of coastal waters with directive 76/160/EEC , 1997 .