Various studies have indicated prions (PrPSC) which infect sheep and goats with the fatal transmissible
encephalopathy known as scrapie are able to persist in soil for years without losing their pathogenic activity. Dissemination of prions into the environment can occur from several sources: mainly, infectious placenta or amniotic fluid of sheep and possibly environmental contamination by saliva or excrement. Confirmatory testing for scrapie can only be achieved by applying
immunohistochemistry of disease-associated prion protein (PrPSC) to tissues collected
post mortem, including
obex (a
brainstem structure),
retropharyngeal lymph node and
palatine tonsil. A live animal diagnostic, not confirmatory, test was approved in 2008 for immunochemistry testing on rectal biopsy-derived lymphoid tissue by USDA. Natural
transmission of scrapie in the field seems to occur via the alimentary tract in the majority of cases, and scrapie-free sheep flocks can become infected on pastures where outbreaks of scrapie had been observed before. These findings point to a sustained contagion in the environment, notably in the soil. Prion concentration in birth fluids does not alter the
infectivity of the prions. Naturally or experimentally infected does and ewes transmit the infection to the lambs, even when placentas have little PrPSC. PrPSC is shed at a higher percentage in sheep placentas (52–72%) than in goat placenta (5–10%) in study trials at the USDA Agricultural Research Service. Detectable PrPSC has been reported in the
feces of sheep both in the terminal and the early preclinical stages of the disease, suggesting the prions are likely to be shed into the environment throughout the course of the disease. Several sources of prions in feces could be postulated, including environmental ingestion and swallowing infected saliva; however, the most likely source is shedding from the gut-associated
lymphoid tissue. Ruminant animals have specialized
Peyer's patches that, throughout the length of the
ileum, amount to about 100,000 follicles, and all of these could be infected and shedding prions into the
lumen. Scrapie prions have been found in the Peyer's patches of naturally infected asymptomatic lambs as young as four months of age.
Exposure through contaminated vaccines •
Contaminated Louping-ill vaccine, known as the
1935 Moredun Louping-ill Vaccine Disaster. More than 1,500 sheep developed scrapie following vaccination. The vaccine was made using formalin-treated sheep brain tissue unknowingly contaminated with scrapie agent. Subsequent investigations showed that intracerebral inoculation of brain and spinal cord tissue from scrapie-infected sheep led to scrapie development in 60% of inoculated sheep, suggesting the presence of a filtrable virus as the probable infective agent. • '
Contaminated Mycoplasma agalactiae
vaccine'. Sudden outbreaks in Italy in 1997 and 1998 were attributed to the administration of a contaminated vaccine, as the brain lesions and polymorphism in the affected animals were similar to those exposed to the same vaccine but different from those in unvaccinated sheep with scrapie. Molecular typing revealed the presence of two prion strains in vaccinated animals, suggesting accidental intra- and interspecies transmission due to the vaccine.
Exposure through contaminated soil Ingestion of soil by grazing sheep has been measured in two soil types, at two stocking rates, and over two grazing seasons. Animals ingested up to 400 g soil per kg of body weight between May and November. Rainfall and stocking rate emerged as factors influencing ingestion. The effect of soil type and vegetation type was less evident. The average weight of an adult sheep is around 250 pounds. If an adult sheep ate 400 g/kg of soil as predicted by D. McGrath
et al., then the average sheep would ingest about 45,000 g over six months, or 251 g per day. Assuming the soil was contaminated with prions (PrPSC) from feces or birth fluids, then potentially the sheep would become infected. The concentration of the prions in the soil is uncertain, and concentration is not directly
proportional to infectivity. Factors affecting prion infectivity in the soil have been shown to include the length of time in the soil and the binding abilities of the soil. For a detailed
risk assessment of scrapie-contaminated soil, it was of major importance to analyze whether the detectable PrPSc in the soil extracts still exhibited oral infectivity after incubation times up to 29 months. A
bioassay with
Syrian hamsters was performed by feeding the animals with contaminated soil or
aqueous soil extracts that had been collected after soil incubation for 26 and 29 months, respectively. Hamsters fed with contaminated soil exhibited their first scrapie-associated symptoms at two weeks to six months (95% CI) after the first feeding. The hamsters reached the terminal stage of scrapie at five to 21 months (95% CI) after the first feeding. This indicated substantial amounts of persistent infectivity in soil that had been incubated for 26 and 29 months. The binding abilities of different soil types have been shown to enhance disease penetrance into a population. Soil containing the common clay mineral
montmorillonite (Mte) and
kaolinite (Kte) binds more effectively with the prions than soil containing
quartz.
Exposure through contaminated hay mites "With scrapie, the archetypical TSE, which is a natural disease in sheep and goats, the disease can appear suddenly in a flock in the absence of any known exposure to infected flocks (Palsson, 1979). Finally, fields in Iceland, that were left empty for up to 3 years after the destruction of scrapie-infected flocks, were repopulated with known scrapie-free sheep, and some of the sheep in this latter group subsequently developed scrapie (Palsson, 1979). This last 'experiment in nature' has yielded similar results a number of times in Iceland and the United Kingdom. In one Icelandic farm, flocks have been eradicated three times; each time, the farm was left without sheep for 2 years, and after restocking with sheep from scrapie-free areas, the disease reappeared. Several years ago, a suggestion was made (S Sigurdarson, personal communication) that hay mites would be a good candidate as a vector for scrapie; this led to the infection of mice with mite samples prepared from hay obtained from five Icelandic farms. Ten of these 71 mice became sick after injection with mite preparations from three of the five farms (Wisniewski et al, 1996; Rubenstein et al, 1998). The incubation periods ranged from 340 days to 626 days, and these mice had the protease-resistant form PrpSc, of a host-coded glycoprotein, PrPc. The protease-resistant form is a marker of TSE disease (Prusiner, 1991; Parchi et al, 1996). For some of these clinically positive mice, the banding pattern on
WB analysis was unique (Wisniewski et al, 1996; Rubenstein et al, 1998)."
Transmission summary Prions (PrPSc) are shed from sheep and goats in birth fluids, feces, and other excrement. The concentration of the prions is uncertain, but is not directly proportional to infectivity. Sheep ingest a considerable amount of soil, so soil represents a plausible environmental reservoir of scrapie prions, which can persist in the environment for years. Longevity of the prions and the attachment of soil particles likely influences the persistence and infectivity of prions in the environment. Effective methods of inactivating prions in the soil are currently lacking, and the effects of natural degradation mechanisms on prion infectivity are largely unknown. An improved understanding of the processes affecting the mobility, persistence and
bioavailability of prions in soil is needed for the management of prion-contaminated environments. A system for estimating the prion-binding capacity of soil on farms using simple soil analysis may allow an estimate of the prion risk in the environment, and whether altering prion binding by the use of soil amendments may help to mitigate the infectious prions.
Lichens, specifically,
Parmelia sulcata,
Cladonia rangiferina and
Lobaria pulmonaria, may have potential for reducing the number of prions because some lichen species contain
proteases that show promise in breaking down the prion. Further work to clone and characterize the proteases, assess their effects on prion infectivity, and determine which component organism or organisms present in lichens produce or influence the protease activity is warranted and is currently under investigation. == Genetics ==