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Soil Enhances Mad Cow BSE
Prion Oral Infectivity By 700%
From Terry S. Singeltary Sr
flounder9@verizon.net
7-7-7
 
Oral Transmissibility of Prion Disease Is Enhanced by Binding to Soil Particles "We observed an almost 700-fold difference"
 
Soil Particles Found To
Boost Prion's Capacity To Infect
By Terry Devitt
7-6-7
 
The rogue proteins that cause chronic wasting disease (CWD) exhibit a dramatic increase in their infectious nature when bound to common soil particles, according to a new study.
 
Writing in the journal Public Library of Science (PLoS) Pathogens, a group led by University of Wisconsin-Madison prion expert Judd Aiken reports that prions, the protein agents of a family of fatal brain disorders, bind tightly to a common soil mineral and significantly increase the oral transmissibility of the agent.
 
The finding is important because it may help explain how chronic wasting disease and scrapie persist in the environment and spread efficiently in animal populations.
 
"We found a huge difference between infectious agent alone and infectious agent bound to these soil particles," says Aiken, the senior author of the new study and a professor of comparative biosciences in the UW-Madison School of Veterinary Medicine. "We observed an almost 700-fold difference" in the rate of infection.
 
Prions are an abnormal form of a protein produced normally by the body. Tough as nails, they can persist in the environment for long periods of time and retain their infectious capabilities. It is believed that prions may persist in the soil around the carcasses of dead animals and other locations where infected animals shed the protein in body fluids.
 
"These disease agents can stay out there for years and stay infectious," Aiken explains.
 
And herbivores such as deer and sheep, which are susceptible to prion infection, tend to consume a fair amount of dirt daily as they graze and forage. They are also known to consume soil as a source of minerals. Mineral licks are frequented by many animals, raising the prospect that the agents may become concentrated in the soil.
 
Relatively little is known about the routes of prion transmission in animals, but the new Wisconsin study may help to resolve one puzzle: Oral transmission of prions, says Aiken, tends not to be very efficient.
 
"This is a dichotomy in our field, and maybe (the new research) is part of the answer."
 
In their studies, the Wisconsin researchers looked at the ability of prions to bind to different types of common soil minerals. One, known as montmorillonite, is a type of clay and prions seem to have a special affinity for latching onto the microscopic particles.
 
"We expected the binding of the montmorillonite to be the highest among the minerals we examined. However, we were surprised by the strength of the binding," notes Joel Pedersen, a UW-Madison professor of soil science who helped direct the new study.
 
The Wisconsin team also looked at the ability of the prion to bind to two other common soil minerals: quartz and kaolinite, another common clay mineral.
 
"We found binding of the abnormal protein to all three," says Aiken, "but the binding to montmorillonite was very avid, very tight. We found it very difficult to remove the prions from the montmorillonite."
 
Feeding the prion-mineral mix to hamsters, a common animal model for prion disease, Aiken's team expected to see a lower rate of infection than animals dosed with pure agent. Surprisingly, prions bound to montmorillonite were significantly more infectious than prions alone.
 
"We thought the binding might decrease infectivity," Aiken explains. "In each case, you add montmorillonite and we get more animals sicker and quicker than in the absence of montmorillonite clay."
 
What is occurring in soils in the woods and on the farm is unknown, says Pedersen, but the new findings may help begin to answer some key questions about how prions survive in the soil and retain their infectious nature, sometimes for years.
 
In the case of scrapie, the prion disease of sheep, observations of sheep pastures in the United Kingdom and Iceland have shown that animals introduced into pastures that once held infected animals could become infected. Infectivity of prions was also enhanced when they were bound to wh ole soil.
 
"Since the 1940s it's been known that 'infected pastures' have the ability to infect new animals," according to Aiken.
 
Pedersen notes that soils are a complex mixture of organic and inorganic components that vary across the landscape and that scientists are just beginning to tease out factors in soils that may contribute to transmissibility. The new study implies, he says, "that some soils may promote the transmission of the prion agent more readily than others."
 
Why that's the case is unknown, Pedersen explains, but the Wisconsin team is exploring several hypotheses: that the soil particles might somehow protect the prion from degradation in the digestive system, that prions bound to clay might change the route or degree of uptake of the agent, or that the mineral somehow alters the size of prion aggregates, which have been shown to be more infectious than prions alone.
 
Aiken emphasizes there's still much to learn about routes of prion transmission, and the role of soil is just beginning to be explored.
 
"Soil is a very complex medium and we don't know what the agent is binding to" in natural or agricultural settings, Aiken says. "We do know that soil is not the only way it transmits. Animal-to-animal transmission is important, too."
 
In addition to Aiken and Pedersen, authors of the PLoS Pathogens paper include Christopher J. Johnson, Rick J. Chappell and Debbie McKenzie. The work was supported by a grant from the U.S. Department of Defense.
 
http://www.news.wisc.edu/13918
 
 
Oral Transmissibility of Prion Disease Is Enhanced by Binding to Soil Particles
 
Christopher J. Johnson1,2, Joel A. Pedersen3, Rick J. Chappell4, Debbie McKenzie2, Judd M. Aiken1,2*
 
1 Program in Cellular and Molecular Biology, University of Wisconsin-Madison, Madison, Wisconsin, United States of America, 2 Department of Comparative Biosciences, School of Veterinary Medicine, University of Wisconsin-Madison, Madison, Wisconsin, United States of America, 3 Department of Soil Science and Molecular and Environmental Toxicology Center, University of Wisconsin-Madison, Madison, Wisconsin, United States of America, 4 Biostatistics and Medical Informatics, University of Wisconsin Medical School, Madison, Wisconsin, United States of America
 
Soil may serve as an environmental reservoir for prion infectivity and contribute to the horizontal transmission of prion diseases (transmissible spongiform encephalopathies [TSEs]) of sheep, deer, and elk. TSE infectivity can persist in soil for years, and we previously demonstrated that the disease-associated form of the prion protein binds to soil particles and prions adsorbed to the common soil mineral montmorillonite (Mte) retain infectivity following intracerebral inoculation. Here, we assess the oral infectivity of Mte- and soil-bound prions. We establish that prions bound to Mte are orally bioavailable, and that, unexpectedly, binding to Mte significantly enhances disease penetrance and reduces the incubation period relative to unbound agent. Cox proportional hazards modeling revealed that across the doses of TSE agent tested, Mte increased the effective infectious titer by a factor of 680 relative to unbound agent. Oral exposure to Mte-associated prions led to TSE development in experimental animals even at doses too low to produce clinical symptoms in the absence of the mineral. We tested the oral infectivity of prions bound to three whole soils differing in texture, mineralogy, and organic carbon content and found soil- bound prions to be orally infectious. Two of the three soils increased oral transmission of disease, and the infectivity of agent bound to the third organic carbon-rich soil was equivalent to that of unbound agent. Enhanced transmissibility of soil-bound prions may explain the environmental spread of some TSEs despite the presumably low levels shed into the environment. Association of prions with inorganic microparticles represents a novel means by which their oral transmission is enhanced relative to unbound agent.
 
 
snip...
 
 
Discussion These experiments address the critical question of whether soil particle­bound prions are infectious by an environmentally relevant exposure route, namely, oral ingestion. Oral infectivity of soil particle­bound prions is a conditio sine qua non for soil to serve as an environmental reservoir for TSE agent. The maintenance of infectivity and enhanced transmissibility when TSE agent is bound to the common soil mineral Mte is remarkable given the avidity of the PrPTSE­Mte interaction [22]. One might expect the avid interaction of PrPTSE with Mte to result in the mineral serving as a sink, rather than a reservoir, for TSE infectivity. Our results demonstrate this may not be the case. Furthermore, sorption of prions to complex whole soils did not diminish bioavailability, and in two of three cases promoted disease transmission by the oral route of exposure. While extrapolation of these results to environmental conditions must be made with care, prion sorption to soil particles clearly has the potential to increase disease transmission via the oral route and contribute to the maintenance of TSE epizootics.
 
Two of three tested soils potentiated oral prion disease transmission. The reason for increased oral transmissibility associated with some, but not all, of the soils remains to be elucidated. One possibility is that components responsible for enhancing oral transmissibility were present at higher levels in the Elliot and Bluestem soils than in the Dodge soil. The major difference between the Dodge soil and the other two soils was the extremely high natural organic matter content of the former (34%, [22]). The Dodge and Elliot soils contained similar levels of mixed-layer illite/smectite, although the contribution of smectite layers was higher in the Dodge soil (14%­16%, [22]). The organic matter present in the Dodge soil may have obstructed access of PrPTSE to sorption sites on smectite (or other mineral) surfaces.
 
The mechanism by which Mte or other soil components enhances the oral transmissibility of particle-bound prions remains to be clarified. Aluminosilicate minerals such as Mte do not provoke inflammation of the intestinal lining [39]. Although such an effect is conceivable for whole soils, soil ingestion is common in ruminants and other mammals [25]. Prion binding to Mte or other soil components may partially protect PrPTSE from denaturation or proteolysis in the digestive tract [22,40] allowing more disease agent to be taken up from the gut than would otherwise be the case. Adsorption of PrPTSE to soil or soil minerals may alter the aggregation state of the protein, shifting the size distribution toward more infectious prion protein particles, thereby increasing the specific titer (i.e., infectious units per mass of protein) [41]. In the intestine, PrPTSE complexed with soil particles may be more readily sampled, endocytosed (e.g., at Peyer's patches), or persorbed than unbound prions. Aluminosilicate (as well as titanium dioxide, starch, and silica) microparticles, similar in size to the Mte used in our experiments, readily undergo endocytotic and persorptive uptake in the small intestine [42­44]. Enhanced translocation of the infectious agent from the gut lumen into the body may be responsible for the observed increase in transmission efficiency.
 
Survival analysis indicated that when bound to Mte, prions from both BH and purified PrPTSE preparations were more orally infectious than unbound agent. Mte addition influenced the effective titer of infected BH to a lesser extent than purified PrPTSE. Several nonmutually exclusive factors may explain this result: (1) other macromolecules present in BH (e.g., lipids, nucleic acids, other proteins) compete with PrPTSE for Mte binding sites; (2) prion protein is more aggregated in the purified PrPTSE preparation than in BH [45], and sorption to Mte reduces PrPTSE aggregate size, increasing specific titer [41]; and (3) sorption of macromolecules present in BH to Mte influences mineral particle uptake in the gut by altering surface charge or size, whereas the approximately 1,000-fold lower total protein concentration in purified PrPTSE preparations did not produce this effect.
 
We previously showed that other inorganic microparticles (kaolinite and silicon dioxide) also bind PrPTSE [22]. All three types of microparticles are widely used food additives and are typically listed as bentonite (Mte), kaolin (kaolinite), and silica (silicon dioxide). Microparticles are increasingly included in Western diets. Dietary microparticles are typically inert and considered safe for consumption by themselves, do not cause inflammatory responses or other pathologies, even with chronic consumption, and are often sampled in the gut and transferred from the intestinal lumen to lymphoid tissue [39,46,47]. Our data suggest that the binding of PrPTSE to dietary microparticles has the potential to enhance oral prion disease transmission and warrants further investigation.
 
In conclusion, our results provide compelling support for the hypothesis that soil serves as a biologically relevant reservoir of TSE infectivity. Our data are intriguing in light of reports that naïve animals can contract TSEs following exposure to presumably low doses of agent in the environment [5,7­9]. We find that Mte enhances the likelihood of TSE manifestation in cases that would otherwise remain subclinical (Figure 3B and 3C), and that prions bound to soil are orally infectious (Figure 5). Our results demonstrate that adsorption of TSE agent to inorganic microparticles and certain soils alter transmission efficiency via the oral route of exposure.
 
 
snip...full text is here:
 
http://pathogens.plosjournals.org/perlserv/?request=get- document&doi=10.1371/journal.ppat.0030093
 
http://pathogens.plosjournals.org/perlserv/?request=get- pdf&file=10.1371_journal.ppat.0030093-L.pdf
 
http://pathogens.plosjournals.org/perlserv/?request=get- pdf&file=10.1371_journal.ppat.0030093-S.pdf
 
 
--TSS

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