***> CONGRESSIONAL ABSTRACTS PRION CONFERENCE 2018
P69 Experimental transmission of CWD from white-tailed deer to co-housed reindeer
Mitchell G (1), Walther I (1), Staskevicius A (1), Soutyrine A (1), Balachandran A (1)
(1) National & OIE Reference Laboratory for Scrapie and CWD, Canadian Food Inspection Agency, Ottawa, Ontario, Canada.
Chronic wasting disease (CWD) continues to be detected in wild and farmed cervid populations of North America, affecting predominantly white-tailed deer, mule deer and elk. Extensive herds of wild caribou exist in northern regions of Canada, although surveillance has not detected the presence of CWD in this population. Oral experimental transmission has demonstrated that reindeer, a species closely related to caribou, are susceptible to CWD. Recently, CWD was detected for the first time in Europe, in wild Norwegian reindeer, advancing the possibility that caribou in North America could also become infected. Given the potential overlap in habitat between wild CWD-infected cervids and wild caribou herds in Canada, we sought to investigate the horizontal transmissibility of CWD from white-tailed deer to reindeer.
Two white-tailed deer were orally inoculated with a brain homogenate prepared from a farmed Canadian white-tailed deer previously diagnosed with CWD. Two reindeer, with no history of exposure to CWD, were housed in the same enclosure as the white-tailed deer, 3.5 months after the deer were orally inoculated. The white-tailed deer developed clinical signs consistent with CWD beginning at 15.2 and 21 months post-inoculation (mpi), and were euthanized at 18.7 and 23.1 mpi, respectively. Confirmatory testing by immunohistochemistry (IHC) and western blot demonstrated widespread aggregates of pathological prion protein (PrPCWD) in the central nervous system and lymphoid tissues of both inoculated white-tailed deer. Both reindeer were subjected to recto-anal mucosal associated lymphoid tissue (RAMALT) biopsy at 20 months post-exposure (mpe) to the white-tailed deer. The biopsy from one reindeer contained PrPCWD confirmed by IHC. This reindeer displayed only subtle clinical evidence of disease prior to a rapid decline in condition requiring euthanasia at 22.5 mpe. Analysis of tissues from this reindeer by IHC revealed widespread PrPCWD deposition, predominantly in central nervous system and lymphoreticular tissues. Western blot molecular profiles were similar between both orally inoculated white-tailed deer and the CWD positive reindeer. Despite sharing the same enclosure, the other reindeer was RAMALT negative at 20 mpe, and PrPCWD was not detected in brainstem and lymphoid tissues following necropsy at 35 mpe. Sequencing of the prion protein gene from both reindeer revealed differences at several codons, which may have influenced susceptibility to infection.
Natural transmission of CWD occurs relatively efficiently amongst cervids, supporting the expanding geographic distribution of disease and the potential for transmission to previously naive populations. The efficient horizontal transmission of CWD from white-tailed deer to reindeer observed here highlights the potential for reindeer to become infected if exposed to other cervids or environments infected with CWD.
***> Infectious agent of sheep scrapie may persist in the environment for at least 16 years
***> Nine of these recurrences occurred 14–21 years after culling, apparently as the result of environmental contamination, but outside entry could not always be absolutely excluded.
Gudmundur Georgsson,1 Sigurdur Sigurdarson2 and Paul Brown3
Correspondence
1 Institute for Experimental Pathology, University of Iceland, Keldur v/vesturlandsveg, IS-112 Reykjavı´k, Iceland
2 Laboratory of the Chief Veterinary Officer, Keldur, Iceland
3 Bethesda, Maryland, USA
Received 7 March 2006 Accepted 6 August 2006
In 1978, a rigorous programme was implemented to stop the spread of, and subsequently eradicate, sheep scrapie in Iceland. Affected flocks were culled, premises were disinfected and, after 2–3 years, restocked with lambs from scrapie-free areas. Between 1978 and 2004, scrapie recurred on 33 farms. Nine of these recurrences occurred 14–21 years after culling, apparently as the result of environmental contamination, but outside entry could not always be absolutely excluded. Of special interest was one farm with a small, completely self-contained flock where scrapie recurred 18 years after culling, 2 years after some lambs had been housed in an old sheephouse that had never been disinfected. Epidemiological investigation established with near certitude that the disease had not been introduced from the outside and it is concluded that the agent may have persisted in the old sheep-house for at least 16 years.
TITLE: PATHOLOGICAL FEATURES OF CHRONIC WASTING DISEASE IN REINDEER AND DEMONSTRATION OF HORIZONTAL TRANSMISSION
*** DECEMBER 2016 CDC EMERGING INFECTIOUS DISEASE JOURNAL CWD HORIZONTAL TRANSMISSION
SEE;
Back around 2000, 2001, or so, I was corresponding with officials abroad during the bse inquiry, passing info back and forth, and some officials from here inside USDA aphis FSIS et al. In fact helped me get into the USA 50 state emergency BSE conference call way back. That one was a doozy. But I always remember what “deep throat” I never knew who they were, but I never forgot;
Some unofficial information from a source on the inside looking out -
Confidential!!!!
As early as 1992-3 there had been long studies conducted on small pastures containing scrapie infected sheep at the sheep research station associated with the Neuropathogenesis Unit in Edinburgh, Scotland. Whether these are documented...I don't know. But personal recounts both heard and recorded in a daily journal indicate that leaving the pastures free and replacing the topsoil completely at least 2 feet of thickness each year for SEVEN years....and then when very clean (proven scrapie free) sheep were placed on these small pastures.... the new sheep also broke out with scrapie and passed it to offspring. I am not sure that TSE contaminated ground could ever be free of the agent!! A very frightening revelation!!!
---end personal email---end...tss
Infectivity surviving ashing to 600*C is (in my opinion) degradable but infective. based on Bown & Gajdusek, (1991), landfill and burial may be assumed to have a reduction factor of 98% (i.e. a factor of 50) over 3 years. CJD-infected brain-tissue remained infectious after storing at room-temperature for 22 months (Tateishi et al, 1988). Scrapie agent is known to remain viable after at least 30 months of desiccation (Wilson et al, 1950). and pastures that had been grazed by scrapie-infected sheep still appeared to be contaminated with scrapie agent three years after they were last occupied by sheep (Palsson, 1979).
Dr. Paul Brown Scrapie Soil Test BSE Inquiry Document
THURSDAY, FEBRUARY 28, 2019
BSE infectivity survives burial for five years with only limited spread
AD.82: Prion-contaminated plants can transmit prion disease
Sandra J. Pritzkow, Rodrigo Morales, Fabio Moda and Claudio Soto
University of Texas Medical School at Houston; Houston. TX USA
Chronic Wasting Disease (CWD) is a prion disorder affecting deer and elk. The efficient propagation of this disease in captive and free-ranging animals suggest that it may involve horizontal transmission through contaminated environment. It has been shown, that infectious prions can enter the environment through saliva, feces, urine, blood or placenta tissue from infected animals, as well as by carcasses from diseased animals. Various studies have demonstrated that infectious prions bind tightly to soil and remain infectious after years in this material.
We hypothesize that plants, which get in contact with infectious prions, can also play a role on the horizontal transmission of prion diseases. To study whether plants can interact with prions, we analyzed wheat grass roots and leaves incubated with 263K-infected brain homogenate in vitro using the PMCA technique and in vivo in Syrian hamsters. For in vitro analyses, the plant tissue was incubated in serial dilutions of 263K-brain homogenate, washed thoroughly and analyzed for the presence of Prpsc by PMCA. The results show that even highly diluted Prpsc can bind to roots and leaves and sustain the conversion of normal prion protein. Similar experiments are currently ongoing using CWD infected material. In vivo, hamsters were orally infected with leaves or roots incubated in 10% 263K-infected brain homogenate, which were thoroughly washed as well. Hamsters, inoculated with 263K-contaminated roots or leaves, developed typical signs of prion disease, whereas control animals inoculated with non-contaminated plants did not. Prion disease was confirmed by immunohistological and biochemical analyses.
These findings suggest that plants (leaves and roots) can efficiently bind infectious prions and act as carrier of infectivity and may play an important role in horizontal transmission by oral intake of the prion agent.
=====
AD.83: Are plants a potential transmission route for infectious prions?
Jay D. Rasmussen,1,3 Brandon H. Gilroyed,2 Tim Reuter,4 Sandor Dudas,5 Catherine Graham,5 Norman F. Neumann.6 Aru Balachandran,7 Stefanie Czub,5 Nat N. Kav1 and Tim A. McAllister3
'Department of Agricultural; Food and Nutritional Sciences; University of Alberta; Edmonton, AB Canada; 2School of Environmental Sciences; University of Guelph Ridgetown Campus; Ridgetown, ON Canada; 3Agriculture and Aqri-Food Canada; Lethbridge Research Centre; Lethbridge, AB Canada; 4Alberta Agriculture and Rural Development; Agriculture Centre; Lethbridge. AB Canada; 5National and OIE Reference Laboratories of BSE; National Centres for Animal Disease Lethbridge Laboratory; Canadian Food Inspection Agency; Lethbridge. AB Canada; School of Public Health; University of Alberta; Edmonton, AB Canada; 'National and OIE Reference Laboratory for scrapie and CWD; Canadian Food Inspection Agency; Ottawa ON Canada
Plants are capable of absorbing large organic materials such as proteins and microorganisms through their roots. This phenomenon introduces the potential for the uptake of infectious prions from the environment and is a possible route for the distribution of prion diseases in natural habitats. Wheat (Triticum aestivum), a major agricultural crop, was used as a model in our experiments to examine prion uptake by plants. In preliminary experiments, model proteins of similar size (Q prions were used (fluorescently-tagged ovalbumin, FT-OV; recombinant cellular PrP, recPrPC). Plants were grown in sterile media (Murashige and Skoog) for 30-45 d before roots were exposed to a model protein solution for 24 h. Foreign target proteins were detected by fluorescent microscopy (FT-OV) and western blotting (FT-OV and recPrPC). FT-OV was found to enter the root system and translocate to the stem. For recPrPc, no detectable uptake or translocation was found, but instead, a strong binding of recPrPc to the outer root surface was observed. These results suggest that uptake by wheat, although possible, might not be universal for all proteins. The consideration of how different plants may respond and how natural root damage may affect protein transport is important. The model described above was used to determine how infectious prions interact with wheat plants. Wheat roots were exposed for 24 h to Chronic Wasting Disease positive and negative elk brain homogenates that were either digested with proteinase K (PK) or left undigested. Plant extracts were analyzed by western blotting to determine the presence of prion proteins, Bands corresponding to PK-sensitive prions were detected in root extracts, but not in other regions of the plant. These results suggest that, similar to model work with recPrPc, PrPc may bind to the outside of the root, without translocation to other areas of the plant. Current work is investigating the implications of exposure of wheat roots to purified PrPCWD on uptake. Future studies will consider the impact of soil on absorption of PrPCWD by roots. Binding of PrPCWD to the surface of wheat roots as shown for PrPc, would open a new discussion on the distribution of infectious prions in the environment.
=====
AD.81: Detection of prion protein associated with cervid chronic wasting disease in environmental samples
Chad J. Johnson, Christen B. Smith, Michael D. Samuel and Joel A. Pedersen University of Wisconsin; Madison. WI USA
Chronic wasting disease (CWD) is a transmissible spongiform encephalopathy (TSE) or prion disease affecting North American members of the deer family (cervids). The disease agent may enter the environment through decomposition of carcasses and shedding in feces, saliva, and urine. Once in the environment disease associated prion protein (PrPTSE) can bind to soil components and remain bioavailable for extended time periods. Assessment of the environmental load of the disease agent is difficult because relevant levels are below the detection limits of immunochemical methods and bioassay is prohibitively expensive to use as a surveillance technique. Here, we report that a combination of detergent extraction and protein misfolding cyclic amplification with beads (PMCAb) substantially improves the sensitivity of PrPTSE detection in environmental samples. Using this technique we are able to achieve detection limits substantially lower than animal bioassay. Working with amended soils we are able to extract and amplify PrPTSE to detectable levels. We have investigated factors contributing to PMCAb inhibition and methods to circumvent those inhibitions. This technique holds promise for helping to clarify the relative importance of direct and indirect transmission of CWD, assess the effectiveness of environmental remediation, and determine environmental loads of infectious agent.
=====
AD.80: Kinetics of chronic wasting disease prion shedding in cervid saliva and urine
Nicholas J. Haley, Davin Henderson, Glenn C. Telling and Edward A. Hoover
Colorado State University; Fort Collins. CO USA
Efficient horizontal transmission is a unique hallmark of chronic wasting disease (CWD) of deer, elk, and moose. Saliva trans- fer, for example via grazing or mutual grooming, is thought to be the primary mechanism of horizontal transmission, although urine and feces are also thought ro play an important role. It is not known how shortly after exposure an animal may begin shedding PrPCWD, though it has been reported that both clinical and pre-clinical animals may successfully transmit CWD to naive deer. We hypothesized that transmission would occur primarily in end-stage disease, though the purpose of this study was to identify earlier time points during the course of CWD infection in which saliva and urine may carry infectivity. Using both transgenic mouse bioassay and real-rime quaking-induced conversion (RT-QuIC), we evaluated saliva and urine from two experimentally infected white tail deer for which samples were available from multiple time points post-inoculation (p.i.) (e.g., 3, 6 and 12 mo p.i., as well as immediately prior to euthanasia at 24-27 mos). We found that while saliva collected during clinical disease was infectious in mouse bioassay, saliva collected 12 mo p.i., prior to the onset of clinical signs was also variably infectious. Saliva from time points earlier than 12 mo p.i. failed to transmit infection, while urine collected from clinically affected deer had very low potential to transmit infection, as has been reported previously. These findings extend our understanding of CWD shedding in the natural host, and may improve control of CWD transmission in captive and free-ranging settings.
PRION UPDATE VIA VEGETABLE PLANTS FROM THE SOIL
PRION UPDATE VIA VEGETABLE PLANTS FROM THE SOIL
56. Members considered that there is no evidence that crops grown on the land which received composted excreta from BSE-challenged animals pose a TSE risk to humans or animals. One member suggested that, as some of these animals are orally challenged with high doses of BSE-infected materials, and the distribution of infectivity in the digestive system is not completely understood, it might be premature to conclude that there is no infective agent in the manure.
Furthermore, an unpublished study had indicated low level absorption of PrP from soil by tomato plants although it should be noted that this study had not been repeated. Details of this work would be sent to the SEAC Secretary. Dr Matthews explained that most of the manure from animals challenged with high doses of BSE had already been composted and used for coppicing. Members agreed that the risks from disposal of residual manure from experimental animals would be much less than historic risks of on farm contamination from naturally infected animals at the height of the BSE epidemic. ...SNIP...END
2014
Major grain organizations oppose CFIA's control zone approach to chronic wasting disease
In the June newsletter, we reported that CFIA has proposed using a control zone approach to control the spread of Chronic Wasting Disease (CWD).
This would restrict the movement of cereal grain screenings within and out of the primary control zones, those being all of Saskatchewan and parts of southern Alberta.
Since CFIA did not consult the feed industry or any of the key grain industry stakeholders before developing the control zone proposal, a broad range of negative, and presumably unintended consequences have emerged during subsequent analysis by industry.
Therefore, over the past several weeks ANAC has teamed up with other stakeholders including the grain elevator, milling and malting associations to prepare a joint submission to the Minister of Agriculture to delineate the negative economic and logistical impacts of CFIA's proposed control zone approach.
CFIA as the developer of the proposal has not provided the scientific and risk-based evidence to support these extraordinary measures to control CWD.
Thus, our letter to the minister emphasized the fact that restrictions on the movement of grain screenings would be a misdirected attempt to halt the spread of the disease, given the improbability that screenings are in fact a significant disease vector associated with CWD.
We also highlighted to the minister that Canada's reputation as a reliable supplier of grains and oilseeds will be undermined if CFIA's proposal is implemented.
Western Canada supplies cereal crops valued at over $7.0 billion annually to the export market, with the annual value of exports from Saskatchewan and Alberta exceeding $3.6 billion and $1.4 billion respectively.
Moreover, the proposed restrictions would adversely affect at least 7 categories of grain businesses at both the international and domestic levels, including wheat milling, oat milling, malting, ethanol, feed manufacturing, seed cleaning and grain handling.
CFIA's control zone proposal is also unanimously opposed by the cervid farming industry.
Farmers are in agreement that the spread of CWD needs to be controlled, however they support the use of a farmed-based risk management system, which is more consistent with CFIA's mandate to deliver outcome-based solutions.
We are hopeful that the joint submission, signed by the major players in the feed and grain industries, will prompt CIFA to propose an alternative workable solution to control CWD.
2015
Subject: CWD TSE AND UPDATE OF PRION TO PLANTS
This past summer we surveyed three sites within RMNP and collected a total of 32 plants. Plants were collected from both outside and inside enclosures that serve to keep wildlife out and allow for restoration and regrowth of the flora. Plant samples were assayed by PMCA and we are now reporting for the first time the novel detection of PrPCWD from the surface on a number of plants assayed. P183
Novel Detection of PrPCWD on Plants Collected from Rocky Mountain National Park
Aimee Ortega1, Jeffrey Seligman1, Jan Leach2, Mark Zabel1 1Colorado State University, Prion Research Center, Department of Microbiology, Immunology and Pathology, Fort Collins, CO, USA, 2Colorado State University, Department of Bioagricultural Sciences and Pest Management, Fort Collins, CO, USA
Chronic wasting disease (CWD) affects animals such as elk, deer, and moose and has become endemic over the last decade. The disease is one of many transmissible spongiform encephalopathies which occur due to the accumulation of an abnormally folded, proteinase K resistant, form of the normal cellular prion protein PrPC. This abnormally folded form, PrPCWD, seeds conversion of PrPC into PrPCWD and eventually forms amyloid fibrils. The exact mechanisms behind transmission and spread of CWD are unknown but research has shown that it can be spread through h o r i z o n t a l , v e r t i c a l , and i n d i r e c t / environmental routes. PrPCWD has been found in both soil and water. Additionally, PrPCWD is very resistant to degradation which makes it stable in the environment for long periods of time. A study has shown that the
Prion2015 Program Guide 29
abnormal prion protein can remain viable in the environment for as long as 16 years. We wanted to further explore the latter and determine whether prions could be detected in grasses and other plants in Rocky Mountain National Park (RMNP) by use of the protein misfolding cyclic amplification (PMCA) assay.
This past summer we surveyed three sites within RMNP and collected a total of 32 plants. Plants were collected from both outside and inside enclosures that serve to keep wildlife out and allow for restoration and regrowth of the flora. Plant samples were assayed by PMCA and we are now reporting for the first time the novel detection of PrPCWD from the surface on a number of plants assayed.
P195 Chronic wasting disease prions detected during early stages of infection by mbPMCA in tissues from white-tailed deer o r a l l y inoculated with f r e e and microparticle-bound prions
Alexandra Chesney1, Chad Johnson1, Tracy Nichols2, Hannah Kornely1, Dania Shoukfeh1, Joel Pedersen1
1University of Wisconsin, Madison, WI, USA, 2United States Department of Agriculture (USDA), Animal and Plant Health Inspection Service (APHIS), Wildlife Services (WS), National Wildlife Research Center (NWRC), Fort Collins, CO, USA
Enhanced oral transmission of rodenta d a p t e d p r i o n d i s e a s e has been demonstrated with the disease agent bound to several types of mineral microparticles; however, the generalizability of this finding to ruminants has not been established. Contaminated soil is believed to represent a reservoir for environmental prions and may contribute to horizontal transmission of chronic wasting disease (CWD) in captive and wild cervid populations. Here, we examined the impact of CWD agent association with microparticles o f montmorillonite, an aluminosilicate clay
Prion2015 Program Guide 35
mineral that showed the largest disease transmission enhancement in rodent bioassays, on early disease in orally inoculated white-tailed deer. Amplification of prions by PMCA has been achieved from various contaminated organs and excretions at late stages in disease. Using microplatebased PMCA (mbPMCA), we detected different accumulation patterns in white-tailed deer tissues 42 days after oral inoculation with CWD prions bound to montmorillonite. We expected mbPMCA to be more sensitive than immunohistochemistry (IHC) to determine prion accumulations in tissues. Through evaluation of mb-PMCA positive tissues, we found that mbPMCA is more sensitive than IHC by at least a factor of 106.3, and detected CWD prions in multiple tissue types that were negative by IHC. These findings suggest that microparticles can enhance the transmission of CWD in white-tailed deer and also demonstrates the consistency and high-throughput utility of the mbPMCA assay. Furthermore, our results indicate that enhanced transmission of microparticle-bound CWD agent warrants consideration in evaluating the relative importance o f d i r e c t and i n d i r e c t (environmental) transmission of CWD in natural populations and in disease management.
P.157: Uptake of prions into plants Christopher Johnson1, Christina Carlson1, Matthew Keating1,2, Nicole Gibbs1, Haeyoon Chang1, Jamie Wiepz1, and Joel Pedersen1 1USGS National Wildlife Health Center; Madison, WI USA; 2University of Wisconsin - Madison; Madison, WI USA Soil may preserve chronic wasting disease (CWD) and scrapie infectivity in the environment, making consumption or inhalation of soil particles a plausible mechanism whereby na€ıve animals can be exposed to prions. Plants are known to absorb a variety of substances from soil, including whole proteins, yet the potential for plants to take up abnormal prion protein (PrPTSE) and preserve prion infectivity is not known. In this study, we assessed PrPTSE uptake into roots using laser scanning confocal microscopy with fluorescently tagged PrPTSE and we used serial protein misfolding cyclic amplification (sPMCA) and detect and quantify PrPTSE levels in plant aerial tissues. Fluorescence was identified in the root hairs of the model plant Arabidopsis thaliana, as well as the crop plants alfalfa (Medicago sativa), barley (Hordeum vulgare) and tomato (Solanum lycopersicum) upon exposure to tagged PrPTSE but not a tagged control preparation. Using sPMCA, we found evidence of PrPTSE in aerial tissues of A. thaliana, alfalfa and maize (Zea mays) grown in hydroponic cultures in which only roots were exposed to PrPTSE. Levels of PrPTSE in plant aerial tissues ranged from approximately 4 £ 10 ¡10 to 1 £ 10 ¡9 g PrPTSE g ¡1 plant dry weight or 2 £ 105 to 7 £ 106 intracerebral ID50 units g ¡1 plant dry weight. Both stems and leaves of A. thaliana grown in culture media containing prions are infectious when intracerebrally-injected into mice.
***Our results suggest that prions can be taken up by plants and that contaminated plants may represent a previously unrecognized risk of human, domestic species and wildlife exposure to prions.
===========
***Our results suggest that prions can be taken up by plants and that contaminated plants may represent a previously unrecognized risk of human, domestic species and wildlife exposure to prions.
*** SEE ; Friday, May 15, 2015 Grass Plants Bind, Retain, Uptake, and Transport Infectious Prions Report
DISCUSSION
This study shows that plants can efficiently bind prions contained in brain extracts from diverse prion infected animals, including CWD-affected cervids. PrPSc attached to leaves and roots from wheat grass plants remains capable of seeding prion replication in vitro. Surprisingly, the small quantity of PrPSc naturally excreted in urine and feces from sick hamster or cervids was enough to efficiently contaminate plant tissue. Indeed, our results suggest that the majority of excreted PrPSc is efficiently captured by plants’ leaves and roots. Moreover, leaves can be contaminated by spraying them with a prion-containing extract, and PrPSc remains detectable in living plants for as long as the study wasperformed (several weeks). Remarkably, prion contaminated plants transmit prion disease to animals upon ingestion, producing a 100% attack rate and incubation periods not substantially longer than direct oral administration of sick brain homogenates. Finally, an unexpected but exciting result was that plants were able to uptake prions from contaminated soil and transport them to aerial parts of the plant tissue. Although it may seem farfetched that plants can uptake proteins from the soil and transport it to the parts above the ground, there are already published reports of this phenomenon (McLaren et al., 1960; Jensen and McLaren, 1960; Paungfoo-Lonhienne et al., 2008). The high resistance of prions to degradation and their ability to efficiently cross biological barriers may play a role in this process. The mechanism by which plants bind, retain, uptake, and transport prions is unknown. Weare currently studying the way in which prions interact with plants using purified, radioactively labeled PrPSc to determine specificity of the interaction, association constant, reversibility, saturation, movement, etc.
Epidemiological studies have shown numerous instances of scrapie or CWD recurrence upon reintroduction of animals on pastures previously exposed to prion-infected animals. Indeed, reappearance of scrapie has been documented following fallow periods of up to 16 years (Georgsson et al., 2006), and pastures were shown to retain infectious CWD prions for at least 2 years after exposure (Miller et al., 2004). It is likely that the environmentally mediated transmission of prion diseases depends upon the interaction of prions with diverse elements, including soil, water, environmental surfaces, various invertebrate animals, and plants. However, since plants are such an important component of the environment and also a major source of food for many animal species, including humans, our results may have far-reaching implications for animal and human health. Currently, the perception of the risk for animal-to-humanprion transmissionhas beenmostly limited to consumption or exposure to contaminated meat; our results indicate that plants might also be an important vector of transmission that needs to be considered in risk assessment.
snip...see full text here ;
Grass Plants Bind, Retain, Uptake, and Transport Infectious Prions
Friday, September 27, 2013
Uptake of Prions into Plants
Terry S. Singeltary Sr. Declares a DECLARATION OF EXTRAORDINARY EMERGENCY DUE TO A FOREIGN ANIMAL DISEASE TRANSMISSIBLE SPONGIFORM ENCEPHALOPATHY TSE PRION CHRONIC WASTING DISEASE CWD IN THE UNITED STATES AND NORTH AMERICA.
The elephant in the room I was speaking of that we all have missed was the feed, yes we all know of ruminant and non ruminant protein and risk factors there from with TSE Prion disease, but we missed the rest of the feed i.e. FEED GRAINS. YES, science has shown in the past, and now recently, the shedding of the CWD TSE Prion into the environment is indeed a risk factor, and for all the grains and such that goes into feed, even hay, hell, Norway does not require any APHIS-Veterinary Services certification for the import of hay/straw. see for yourself ;
Hay/Straw
*** Norway does not require any APHIS-Veterinary Services certification for the import of hay/straw. ***
you add up all the other grains in feed, and then wonder about exposure to the CWD TSE PRION from cervid and risk factor from the CWD there from via shedding or right down to the soil these grains were grown in, and you have a world of problems.
see ;
Feed Grains Data: Yearbook Tables Created March 10, 2016
Updates of this data, and data covering more years and countries, can be found at
U.S. Acreage, Production, Yield, and Farm Price Table 1--Corn, sorghum, barley, and oats: Planted acreage, harvested acreage, production, yield, and farm price World Production, Supply, and Disappearance
Table 2--Foreign coarse grains: Supply and disappearance Table 3--Feed grains (corn, sorghum, barley, and oats): Supply and disappearance U.S. Supply and Disappearance Table 4--Corn: Supply and disappearance Table 5--Sorghum: Supply and disappearance Table 6--Barley: Supply and disappearance Table 7--Oats: Supply and disappearance U.S. Production, Yield, and Stocks Table 8--Hay: Production, harvested acreage, yield, and stocks Domestic and International Prices Table 9--Corn and sorghum: Average prices received by farmers, United States Table 10--Barley and oats: Average prices received by farmers, United States Table 11--Hay: Average prices received by farmers, United States Table 12--Corn: Cash prices at principal markets Table 13--Sorghum: Cash prices at principal markets Table 14--Barley and oats: Cash prices at principal markets Table 15--Feed-price ratios for livestock, poultry, and milk Table 16--Byproduct feeds: Average wholesale price, bulk, specified markets Table 17--Processed corn products: Quoted market prices Exports and Imports Table 18--U.S. corn and sorghum exports Table 19--U.S. barley and oats exports Table 20--U.S. corn and sorghum imports Table 21--U.S. barley and oats imports Table 22--U.S. corn and sorghum exports by selected destinations Table 23--U.S. barley and oats exports by selected destinations Table 24--U.S. corn and sorghum imports by selected sources Table 25--U.S. barley and oats imports by selected sources Table 26--U.S. white corn exports by selected destinations Table 27--World coarse grain trade: Selected exporters and importers by commodity Rail rates and shipments Table 28--Rail rates and grain shipments Processed feeds and animal unit indexes Table 29--Processed feeds: Quantities fed and feed per grain-consuming animal unit Table 30--Indexes of feed consuming animal units Feed, seed, and industrial uses Table 31—Corn: Feed, seed, and industrial uses Exports and imports for ethyl alcohol and brewers’ and distillers’ dregs and waste Table 32—U.S. exports of ethyl alcohol by selected destinations Table 33—U.S. imports of ethyl alcohol by selected sources Table 34—U.S. exports of brewers’ and distillers’ dregs and waste by selected commodities Table 35—U.S. imports of brewers’ and distillers’ dregs and waste by selected sources Contact: Thomas Capehart at tcapehart+A25@ers.usda.gov
‘’The statement you were concerned about was corrected to "One sorghum DDGS out of 168 DG samples was contaminated with animal protein prohibited for use in ruminant feed and was channeled to poultry feed."
Subject: Re: TEXAS CONFIRMATION OF BOVINE SPONGIFORM ENCEPHALOPATHY BSE TSE PRION IN ONE SAMPLE OF SORGHUM DDGS OUT OF 168 DG SAMPLES
snip...see full text ;
Using in vitro Prion replication for high sensitive detection of prions and prionlike proteins and for understanding mechanisms of transmission.
Claudio Soto Mitchell Center for Alzheimer's diseases and related Brain disorders, Department of Neurology, University of Texas Medical School at Houston.
Prion and prion-like proteins are misfolded protein aggregates with the ability to selfpropagate to spread disease between cells, organs and in some cases across individuals. I n T r a n s m i s s i b l e s p o n g i f o r m encephalopathies (TSEs), prions are mostly composed by a misfolded form of the prion protein (PrPSc), which propagates by transmitting its misfolding to the normal prion protein (PrPC). The availability of a procedure to replicate prions in the laboratory may be important to study the mechanism of prion and prion-like spreading and to develop high sensitive detection of small quantities of misfolded proteins in biological fluids, tissues and environmental samples. Protein Misfolding Cyclic Amplification (PMCA) is a simple, fast and efficient methodology to mimic prion replication in the test tube. PMCA is a platform technology that may enable amplification of any prion-like misfolded protein aggregating through a seeding/nucleation process. In TSEs, PMCA is able to detect the equivalent of one single molecule of infectious PrPSc and propagate prions that maintain high infectivity, strain properties and species specificity. Using PMCA we have been able to detect PrPSc in blood and urine of experimentally infected animals and humans affected by vCJD with high sensitivity and specificity. Recently, we have expanded the principles of PMCA to amplify amyloid-beta (Aβ) and alphasynuclein (α-syn) aggregates implicated in Alzheimer's and Parkinson's diseases, respectively. Experiments are ongoing to study the utility of this technology to detect Aβ and α-syn aggregates in samples of CSF and blood from patients affected by these diseases.
=========================
***>>> Recently, we have been using PMCA to study the role of environmental prion contamination on the horizontal spreading of TSEs. These experiments have focused on the study of the interaction of prions with plants and environmentally relevant surfaces. Our results show that plants (both leaves and roots) bind tightly to prions present in brain extracts and excreta (urine and feces) and retain even small quantities of PrPSc for long periods of time. Strikingly, ingestion of prioncontaminated leaves and roots produced disease with a 100% attack rate and an incubation period not substantially longer than feeding animals directly with scrapie brain homogenate. Furthermore, plants can uptake prions from contaminated soil and transport them to different parts of the plant tissue (stem and leaves). Similarly, prions bind tightly to a variety of environmentally relevant surfaces, including stones, wood, metals, plastic, glass, cement, etc. Prion contaminated surfaces efficiently transmit prion disease when these materials were directly injected into the brain of animals and strikingly when the contaminated surfaces were just placed in the animal cage. These findings demonstrate that environmental materials can efficiently bind infectious prions and act as carriers of infectivity, suggesting that they may play an important role in the horizontal transmission of the disease.
========================
Since its invention 13 years ago, PMCA has helped to answer fundamental questions of prion propagation and has broad applications in research areas including the food industry, blood bank safety and human and veterinary disease diagnosis.
172. Establishment of PrPCWD extraction and detection methods in the farm soil
Kyung Je Park, Hoo Chang Park, In Soon Roh, Hyo Jin Kim, Hae-Eun Kang and Hyun Joo Sohn
Foreign Animal Disease Division, Animal and Plant Quarantine Agency, Gimcheon, Gyeongsangbuk-do, Korea
ABSTRACT
Introduction:
Transmissible spongiform encephalopathy (TSE) is a fatal neurodegenerative disorder, which is so-called as prion diseases due to the causative agents (PrPSc). TSEs are believed to be due to the template-directed accumulation of disease-associated prion protein, generally designated PrPSc. Chronic wasting disease (CWD) is the prion disease that is known spread horizontally. CWD has confirmed last in Republic of Korea in 2016 since first outbreak of CWD in 2001. The environmental reservoirs mediate the transmission of this disease. The significant levels of infectivity have been detected in the saliva, urine, and faeces of TSE-infected animals. Soil can serve as a stable reservoir for infectious prion proteins. We found that PrPCWD can be extracted and detected in CWD contaminated soil which has kept at room temperature until 4 years after 0.001 ~ 1% CWD exposure and natural CWD-affected farm soil through PBS washing and sPMCAb.
Materials and Methods: Procedure of serial PMCAb.
CWD contaminated soil which has kept at room temperature (RT) for 1 ~ 4 year after 0.001%~1% CWD brain homogenates exposure for 4 months collected 0.14 g. The soil was collected by the same method once of year until 4 year after stop CWD exposure. We had conducted the two steps. There are two kinds of 10 times washing step and one amplification step. The washing step was detached PrPSc from contaminated soil by strong vortex with maximum rpm. We harvest supernatant every time by 10 times. As the other washing step, the Washed soil was made by washing 10 times soil using slow rotator and then harvest resuspended PBS for removing large impurity material. Last step was prion amplification step for detection of PrPCWD in soil supernatant and the washed soil by sPMCAb. Normal brain homogenate (NBH) was prepared by homogenization of brains with glass dounce in 9 volumes of cold PBS with TritonX-100, 5 mM EDTA, 150 mM NaCl and 0.05% Digitonin (sigma) plus Complete mini protease inhibitors (Roche) to a final concentration of 5%(w/v) NBHs were centrifuged at 2000 g for 1 min, and supernatant removed and frozen at −70 C for use. CWD consisted of brain from natural case in Korea and was prepared as 10%(w/v) homogenate. Positive sample was diluted to a final dilution 1:1000 in NBH, with serial 3:7 dilutions in NBH. Sonication was performed with a Misonix 4000 sonicator with amplitude set to level 70, generating an average output of 160W with two teflon beads during each cycle. One round consisted of 56 cycles of 30 s of sonication followed 9 min 30 s of 37°C incubation. Western Blotting (WB) for PrPSc detection. The samples (20 µL) after each round of amplification were mixed with proteinase K (2 mg/ml) and incubated 37°C for 1 h. Samples were separated by SDS-PAGE and transferred onto PVDF membrane. After blocking, the membrane was incubated for 1 h with 1st antibody S1 anti rabbit serum (APQA, 1:3000) and developed with enhanced chemiluminescence detection system.
Results: We excluded from first to third supernatant in view of sample contamination. It was confirmed abnormal PrP amplification in all soil supernatants from fourth to tenth. From 0.01% to 1% contaminated washed soils were identified as abnormal prions. 0.001% contaminated washed soil did not show PrP specific band (Fig 1). The soil was collected by the same method once of year until 4 year after stop CWD exposure. After sPMCAb, there were no PrPCWD band in from second to fourth year 0.001% washed soil. but It was confirmed that the abnormal prion was amplified in the washing supernatant which was not amplified in the washed soil. we have decided to use soil supernatant for soil testing (Fig. 2). After third rounds of amplification, PrPSc signals observed in three out of four sites from CWD positive farm playground. No signals were observed in all soil samples from four CWD negative farm (Fig. 3).
Conclusions: Our studies showed that PrPCWD persist in 0.001% CWD contaminated soil for at least 4 year and natural CWD-affected farm soil. When cervid reintroduced into CWD outbreak farm, the strict decontamination procedures of the infectious agent should be performed in the environment of CWD-affected cervid habitat.
===
186. Serial detection of hematogenous prions in CWD-infected deer
Amy V. Nalls, Erin E. McNulty, Nathaniel D. Denkers, Edward A. Hoover and Candace K. Mathiason
Department of Microbiology, Immunology, and Pathology, Colorado State University, Fort Collins, CO, USA
ABSTRACT
Blood contains the infectious agent associated with prion disease affecting several mammalian species, including humans, cervids, sheep, and cattle. It has been confirmed that sufficient prion agent is present in the blood of both symptomatic and asymptomatic carriers to initiate the amyloid templating and accumulation process that results in this fatal neurodegenerative disease. Yet, to date, the ability to detect blood-borne prions by in vitro methods remains difficult.
We have capitalized on blood samples collected from longitudinal chronic wasting disease (CWD) studies in the native white-tailed deer host to examine hematogenous prion load in blood collected minutes, days, weeks and months post exposure. Our work has focused on refinement of the amplification methods RT-QuIC and PMCA. We demonstrate enhanced in vitro detection of amyloid seeding activity (prions) in blood cell fractions harvested from deer orally-exposed to 300 ng CWD positive brain or saliva.
These findings permit assessment of the role hematogenous prions play in the pathogenesis of CWD and provide tools to assess the same for prion diseases of other mammalian species.
Considering the oral secretion of prions, saliva from CWD-infected deer was shown to transmit disease to other susceptible naïve deer when harvested from the animals in both the prions in the saliva and blood of deer with chronic wasting disease.
of infection, albeit within relatively large volumes of saliva (50 ml). In sheep with preclinical, natural scrapie infections, sPMCA facilitated the detection of PrPSc within buccal swabs throughout most of the incubation period of the disease with an apparent peak in prion secretion around the mid-term of disease progression.70
The amounts of prion present in saliva are likely to be low as indicated by CWD-infected saliva producing prolonged incubation periods and incomplete attack rates within the transgenic mouse bioassay.41
snip...
Indeed, it has also been shown that the scrapie and CWD prions are excreted in urine, feces and saliva and are likely to be excreted from skin. While levels of prion within these excreta/secreta are very low, they are produced throughout long periods of preclinical disease as well as clinical disease. Furthermore, the levels of prion in such materials are likely to be increased by concurrent inflammatory conditions affecting the relevant secretory organ or site. Such dissemination of prion into the environment is very likely to facilitate the repeat exposure of flockmates to low levels of the disease agent, possibly over years.
snip...
Given the results with scrapie-contaminated milk and CWD-contaminated saliva, it seems very likely that these low levels of prion in different secreta/excreta are capable of transmitting disease upon prolonged exposure, either through direct animal-to-animal contact or through environmental reservoirs of infectivity.
the other part, these tissues and things in the body then shed or secrete prions which then are the route to other animals into the environment, so in particular, the things, the secretions that are infectious are salvia, feces, blood and urine. so pretty much anything that comes out of a deer is going to be infectious and potential for transmitting disease.
MONDAY, JUNE 12, 2017
Rethinking Major grain organizations opposition to CFIA's control zone approach to Chronic Wasting CWD TSE Prion Mad Deer Type Disease 2017?
New studies on the heat resistance of hamster-adapted scrapie agent: Threshold survival after ashing at 600°C suggests an inorganic template of replication
Prion Infected Meat-and-Bone Meal Is Still Infectious after Biodiesel Production
Detection of protease-resistant cervid prion protein in water from a CWD-endemic area
A Quantitative Assessment of the Amount of Prion Diverted to Category 1 Materials and Wastewater During Processing
Rapid assessment of bovine spongiform encephalopathy prion inactivation by heat treatment in yellow grease produced in the industrial manufacturing process of meat and bone meals
PPo4-4:
Survival and Limited Spread of TSE Infectivity after Burial
Discussion Classical scrapie is an environmentally transmissible disease because it has been reported in naïve, supposedly previously unexposed sheep placed in pastures formerly occupied by scrapie-infected sheep (4, 19, 20).
Although the vector for disease transmission is not known, soil is likely to be an important reservoir for prions (2) where – based on studies in rodents – prions can adhere to minerals as a biologically active form (21) and remain infectious for more than 2 years (22).
Similarly, chronic wasting disease (CWD) has re-occurred in mule deer housed in paddocks used by infected deer 2 years earlier, which was assumed to be through foraging and soil consumption (23).
Our study suggested that the risk of acquiring scrapie infection was greater through exposure to contaminated wooden, plastic, and metal surfaces via water or food troughs, fencing, and hurdles than through grazing.
Drinking from a water trough used by the scrapie flock was sufficient to cause infection in sheep in a clean building.
Exposure to fences and other objects used for rubbing also led to infection, which supported the hypothesis that skin may be a vector for disease transmission (9).
The risk of these objects to cause infection was further demonstrated when 87% of 23 sheep presented with PrPSc in lymphoid tissue after grazing on one of the paddocks, which contained metal hurdles, a metal lamb creep and a water trough in contact with the scrapie flock up to 8 weeks earlier, whereas no infection had been demonstrated previously in sheep grazing on this paddock, when equipped with new fencing and field furniture.
When the contaminated furniture and fencing were removed, the infection rate dropped significantly to 8% of 12 sheep, with soil of the paddock as the most likely source of infection caused by shedding of prions from the scrapie-infected sheep in this paddock up to a week earlier.
This study also indicated that the level of contamination of field furniture sufficient to cause infection was dependent on two factors: stage of incubation period and time of last use by scrapie-infected sheep.
Drinking from a water trough that had been used by scrapie sheep in the predominantly pre-clinical phase did not appear to cause infection, whereas infection was shown in sheep drinking from the water trough used by scrapie sheep in the later stage of the disease.
It is possible that contamination occurred through shedding of prions in saliva, which may have contaminated the surface of the water trough and subsequently the water when it was refilled.
Contamination appeared to be sufficient to cause infection only if the trough was in contact with sheep that included clinical cases.
Indeed, there is an increased risk of bodily fluid infectivity with disease progression in scrapie (24) and CWD (25) based on PrPSc detection by sPMCA.
Although ultraviolet light and heat under natural conditions do not inactivate prions (26), furniture in contact with the scrapie flock, which was assumed to be sufficiently contaminated to cause infection, did not act as vector for disease if not used for 18 months, which suggest that the weathering process alone was sufficient to inactivate prions.
PrPSc detection by sPMCA is increasingly used as a surrogate for infectivity measurements by bioassay in sheep or mice.
In this reported study, however, the levels of PrPSc present in the environment were below the limit of detection of the sPMCA method, yet were still sufficient to cause infection of in-contact animals.
In the present study, the outdoor objects were removed from the infected flock 8 weeks prior to sampling and were positive by sPMCA at very low levels (2 out of 37 reactions).
As this sPMCA assay also yielded 2 positive reactions out of 139 in samples from the scrapie-free farm, the sPMCA assay could not detect PrPSc on any of the objects above the background of the assay.
False positive reactions with sPMCA at a low frequency associated with de novo formation of infectious prions have been reported (27, 28).
This is in contrast to our previous study where we demonstrated that outdoor objects that had been in contact with the scrapie-infected flock up to 20 days prior to sampling harbored PrPSc that was detectable by sPMCA analysis [4 out of 15 reactions (12)] and was significantly more positive by the assay compared to analogous samples from the scrapie-free farm.
This discrepancy could be due to the use of a different sPMCA substrate between the studies that may alter the efficiency of amplification of the environmental PrPSc.
In addition, the present study had a longer timeframe between the objects being in contact with the infected flock and sampling, which may affect the levels of extractable PrPSc.
Alternatively, there may be potentially patchy contamination of this furniture with PrPSc, which may have been missed by swabbing.
The failure of sPMCA to detect CWD-associated PrP in saliva from clinically affected deer despite confirmation of infectivity in saliva-inoculated transgenic mice was associated with as yet unidentified inhibitors in saliva (29), and it is possible that the sensitivity of sPMCA is affected by other substances in the tested material.
In addition, sampling of amplifiable PrPSc and subsequent detection by sPMCA may be more difficult from furniture exposed to weather, which is supported by the observation that PrPSc was detected by sPMCA more frequently in indoor than outdoor furniture (12).
A recent experimental study has demonstrated that repeated cycles of drying and wetting of prion-contaminated soil, equivalent to what is expected under natural weathering conditions, could reduce PMCA amplification efficiency and extend the incubation period in hamsters inoculated with soil samples (30).
This seems to apply also to this study even though the reduction in infectivity was more dramatic in the sPMCA assays than in the sheep model.
Sheep were not kept until clinical end-point, which would have enabled us to compare incubation periods, but the lack of infection in sheep exposed to furniture that had not been in contact with scrapie sheep for a longer time period supports the hypothesis that prion degradation and subsequent loss of infectivity occurs even under natural conditions.
In conclusion, the results in the current study indicate that removal of furniture that had been in contact with scrapie-infected animals should be recommended, particularly since cleaning and decontamination may not effectively remove scrapie infectivity (31), even though infectivity declines considerably if the pasture and the field furniture have not been in contact with scrapie-infected sheep for several months. As sPMCA failed to detect PrPSc in furniture that was subjected to weathering, even though exposure led to infection in sheep, this method may not always be reliable in predicting the risk of scrapie infection through environmental contamination.
These results suggest that the VRQ/VRQ sheep model may be more sensitive than sPMCA for the detection of environmentally associated scrapie, and suggest that extremely low levels of scrapie contamination are able to cause infection in susceptible sheep genotypes.
Keywords: classical scrapie, prion, transmissible spongiform encephalopathy, sheep, field furniture, reservoir, serial protein misfolding cyclic amplification
Wednesday, December 16, 2015
*** Objects in contact with classical scrapie sheep act as a reservoir for scrapie transmission ***
Journal of Wildlife Diseases, 56(3), 2020, pp. 000–000
Wildlife Disease Association 2020
EFFECT OF ORAL COPPER SUPPLEMENTATION ON SUSCEPTIBILITY IN WHITE-TAILED DEER (ODOCOILEUS VIRGINIANUS) TO CHRONIC WASTING DISEASE
Oral Cu supplementation increased liver Cu concentrations compared to controls but did not affect susceptibility to CWD or survival after natural exposure in the captive white-tailed deer we studied.
TUESDAY, DECEMBER 31, 2019
In Vitro detection of Chronic Wasting Disease (CWD) prions in semen and reproductive tissues of white tailed deer bucks (Odocoileus virginianus
SUNDAY, AUGUST 02, 2015
TEXAS CWD, Have you been ThunderStruck, deer semen, straw bred bucks, super ovulation, and the potential TSE Prion connection, what if?
SUNDAY, AUGUST 02, 2015
TEXAS CWD, Have you been ThunderStruck, deer semen, straw bred bucks, super ovulation, and the potential TSE Prion connection, what if?
SUNDAY, FEBRUARY 16, 2020
Jerking for Dollars, Are Texas Politicians and Legislators Masturbating Deer For Money, and likely spreading CWD TSE Prion?
0 Comments:
Post a Comment
Subscribe to Post Comments [Atom]
<< Home