Heidi H. Petersen 1, Heidi L. Enemark 2, Annette Olsen 1, Mostofa Amin 3 and Anders Dalsgaard 1 (1)Department of Veterinary Disease Biology, University.

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Heidi H. Petersen 1, Heidi L. Enemark 2, Annette Olsen 1, Mostofa Amin 3 and Anders Dalsgaard 1 (1)Department of Veterinary Disease Biology, University of Copenhagen, Frederiksberg, Denmark (2) Section for Bacteriology, Pathology and Parasitology, National Veterinary Institute, Frederiksberg Denmark (3) Department of Agroecology, Faculty of Science and Technology, Aarhus University, Tjele, Denmark CONTAMINATION OF DRINKING WATER with pathogens including Cryptosporidium spp. originates primarily from surface water 1. GROUNDWATER samples are, however, found positive for Cryptosporidium oocysts, e.g. in Germany 2. VERTICAL TRANSPORT through soil might be responsible for the presence of oocysts in groundwater. LIVESTOCK SLURRY contains large volumes of pathogens including Cryptosporidium, and large volumes of slurry are regularly applied to agricultural soil. MANURE MANAGEMENT PRACTICES could influence the oocyst numbers transported through soil as well as the viability of oocysts. THEREFORE, we examined the transport of C. parvum oocysts in intact soil columns following either: Surface application of a liquid fraction of separated pig slurry Surface application of raw pig slurry Injection of raw pig slurry B ackground S tudy Design R esults Slurry separation How manure management affect vertical transport of Cryptosporidium parvum oocysts Area where raw or liquid slurry was applied – 17 cm 2 cm 10 cm 4 cm Area where raw slurry was injected – 10 cm References: 1 Fricker er al. (1998). Adv. Parasitol. 40, ; 2 Gallas-Lindemann et al., (2013) Epidemiol. Infect. 141(1), Sum of total oocysts recovered from all leachate samples collected at all four sampling times (4 L) 2 Back-transformed LS-means estimate per L leachate In general, the recovery rate of oocysts in the leachate was low (see below). However, the majority of the 24 leachate samples collected from each soil column, the following were positive for oocysts: Injected liquid slurry = 21/24 (88%) 0.06% oocysts recovered Injected raw slurry=21/24 (88%)0.02% oocysts recovered Raw slurry surface applied =12/24 (50%)0.01% oocysts recovered C onclusions 20 cm A total of 3.1 x 10 6 C. parvum oocysts were mixed with slurry 6 x Liquid slurry 12 x Raw slurry Slurry applied on top of soil columns 1 L simulated rainfall was applied to the soil columns weekly for 4 weeks Approx. 1 L leachate was collected following each of the weekly rainfalls Oocysts were enumerated and viability was assessed by vital dye staining (DAPI/PI) in the 50 ml leachate following concentration by IMS Soil columns were sectioned and oocysts enumerated in each section Slurry injected into soil columns MANURE MANAGEMENT influences the number of oocysts transported through soil The SEPARATED LIQUID FRACTION OF SLURRY gave rise to the highest number of leached oocysts leached INJECTED RAW SLURRY INJECTED induced a higher number of oocysts in the leachate thancompared to SURFACE APPLIED RAW SLURRY. VIABLE OOCYSTS were revealed during all four weeks in volumes infective for humans ACKNOLEDGEMENTS: This research was supported by a grant from the PATHOS project funded by the Strategic Research Council of Denmark (ENV ). Laboratory technicians Boi-Tien Thi Pham and staff at the Faculty of Agricultural Sciences of Aarhus University are acknowledged for dedicated technical assistance. 61 % of leachate samples contained viable oocysts 39 % of leachate samples had no viable oocysts Viable oocysts were found in leachate collected during all four weeks in all three column types Total numbers of viable oocysts (DAPI+/PI- and DAPI-/PI-) enumerated in all types of leachate samples ranged per 4 L cm P12