Animal Waste, Water Quality and Human Health

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Comparative risk analysis 401Table A10.5 (Continued)Reference Prevalence (%) Concentration NotesHutchison et al.(2004/5)13.5 58 cfu/g (g.m.) C. parvum in fresh composite farm manure, UK.max. = 3.6 × 10 3 cfu/gSheepHutchison et al. (2004/5) 29.2 10 cfu/g (g.m.) C. parvum in fresh composite farm manure, UK.max. = 2.5 × 10 2 cfu/gRyan et al. (2005) 2.6 – AustraliaPoultryFerguson et al. (2009) – – Two studies: (i) prevalence in US 6% (broilers) and27% (layer chickens); (ii) prevalence = 27% (16samples) in The Netherlands. Average shedding rate= 2100 oocysts/g faeces for Netherlands layers.Hutchison et al.(2004/5)“g.m.” = geometric mean, “ave.” = arithmetic mean, “max.” = maximum0 – C. parvum in fresh composite farm manure, UK.
402Animal Waste, Water Quality and Human Health(full descriptions of these studies are of course given in the cited references in thesetables). Note that these studies typically analyse composite samples, rather thanfaecal material from individual animals. Therefore the variation between individualanimals is smoothed somewhat. This is appropriate for risk studies, because faecalcontamination of environmental water typically arises from groups of animals, notfrom an individual animal.PATHOGEN SURVIVAL (T 90 ) AND EFFECT OF SUNLIGHTCampylobacter, E. coli and SalmonellaSinton et al. (2007a) reported inactivation rates of Campy. jejuni, E. coli, and Salm.enterica (inter alia) in bovine faeces on pasture. In the first one to three weeks, therewere increases (up to 1.5 orders of magnitude) in the counts of E. coli (threeseasons) and Salm. enterica (two seasons), but there was none for Campy. jejuni.Thereafter, the counts decreased, giving an average ranking of the times necessaryfor 90% inactivation of Campy. jejuni (6.2 days from deposition) < S. enterica (38days) < E. coli (48 days). Sinton et al. (2007b) studied the inactivation of the samemicroorganisms in river water and seawater. All sunlight inactivation rates, as afunction of were far higher than the corresponding dark rates. All the T 90 valueswere higher in winter than in summer. Seasonal values for Salm. enterica and E. coliwere similar and both were considerably larger than those for Campy. jejuni. Therapid inactivation of Campy. jejuni was attributed to a high susceptibility tophoto-oxidative damage.Giardia and CryptosporidiumOlson et al. (1999) reported that Giardia cysts were noninfective in water, faeces, andsoil following one week of freezing to −4°C and within two weeks at 25°C. At 4°CGiardia cysts were infective for 11 weeks in water, seven weeks in soil, and oneweek in cattle faeces. Cryptosporidium oocysts were more environmentally resistant.At −4°C and 4°C, the oocysts could survive in water and soil for >12 weeks butdegradation was accelerated at 25°C. Cryptosporidium oocysts also were degradedmore rapidly in faeces and in soil containing natural microorganisms. Davies et al.(2005b) reported T 90 for closed non-irradiated soil microcosms ranging from 13–24days at 35 o Cto45–66 days at 20 o C depending on soil type. In laboratory studies ofCrypto. parvum, Ives et al. (2007) reported first-order log 10 inactivation coefficientsranging from k = 0.0088 per day at 5°C to 0.20 per day at 30°C. These correspond toT 90 values of approximately 114 and 5 days respectively [using the first-order
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Emerging Issues in Water and Infect
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World Health Organization and IWA P
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Published on behalf of the World He
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3Zoonotic waterborne pathogen loads
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Zoonotic waterborne pathogen loads
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the cause of a variety of food- and
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4Zoonotic waterbornepathogens in li
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controlling E. coli-associated diar
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5Transport of microbial pollution i
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Transport of microbial pollution in
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7ExposureWill Robertson and Gordon
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Exposure 259main components influen
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Exposure 261rainfall events (Atherh
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Exposure 263contact activities, the
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Exposure 265Table 7.1 Notable studi
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Exposure 267Table 7.2 Notable studi
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Exposure 269water than zoonotic pat
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Exposure 2711999). As suggested by
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Exposure 273leptospirosis is primar
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are severely underreported. As with
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Exposure 277duodenalis in surface w
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Exposure 279Keeley, A. and Faulkner
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Exposure 281Schultz-Fademrecht, C.,
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IndexAgricultural runoff, 122, 168,
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Index 463Biogas, 137-139, 291Bio-se
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Index 465Critical control points, 1
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Index 467290-291, 293, 295, 300, 30
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Index 469Hazard detection, 285Hazar
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Index 471pathogens, 2, 4-14, 17-21,
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Index 473Probiotics, 132-133Protozo
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Index 475Molecular, 16, 19, 22, 27,
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Animal Waste, Water Quality and Human Health

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