Carcass Management During a Mass Animal Health Emergency Draft Programmatic 
Environmental Impact Statement—August 2015
Agency Contact:
Lori P. Miller Senior Staff Officer National Center for Animal Health 
Emergency Management Veterinary Services Animal and Plant Health Inspection 
Service U.S. Department of Agriculture 4700 River Road, Unit 41 Riverdale, MD 
20737–1238 
snip... 
APHIS classifies 
Tier 1 diseases of national concern as those posing the most significant 
threat to animal agriculture in the United States, including African swine fever 
(ASF), avian influenza (AI), classical swine fever (CSF), FMD, and virulent 
Newcastle disease. 
Tier 2 diseases are transmitted primarily by pests, and include heartwater, 
New World screwworm, Rift Valley fever, and Venezuelan equine encephalitis. 
Tier 3 diseases pose less risk and fewer consequences than those in Tiers 1 
and 2. 
Tier 3 diseases include African horse sickness (AHS), contagious bovine 
pleuropneumonia, contagious caprine pleuropneumonia, glanders, melioidiosis, 
henipaviruses (Hendra and Nipah viruses), rinderpest, peste des petits 
ruminants, and tropical bont tick. APHIS excludes from its tiered lists endemic 
diseases already managed in this country (e.g., brucellosis, 2. Livestock 
Disease Issues bovine tuberculosis, and hog cholera, hydatid cysts in liver, 
poultry with low pathogenic avian influenza (LPAI), scrapie, and trichinae). 
(what about atypical Nor-98 Scrapie, typical and atypical Bovine Spongiform 
Encephalopathy BSE, and Chronic Wasting Disease CWD $$$...TSS) 
snip... 
Internationally, a well-devised carcass management plan is viewed as a key 
component of a country's ability to recover from an animal disease outbreak. As 
a member of the World Organization for Animal Health (OIE), the U.S. status for 
communicable diseases (diseases transferred from one animal to another e.g., 
bovine spongiform encephalopathy (BSE), contagious bovine pleuropneumonia 
(CBPP), rinderpest, and FMD) are tracked and reported (OIE, 2015a). Effective 
carcass management within the United States during a FAD outbreak is essential 
to ensure normal international trade relations.
B. Mass Animal Health Emergency Scenarios
snip...
34 III. Affected Environment 
Transmissible spongiform encephalopathy (TSE) diseases, thought to be 
caused by the presence of a misfolded protein (prion) in the animal’s nervous 
tissue, cause slow degeneration of the nervous system, ultimately ending in 
death. TSE in sheep and goats is referred to as scrapie, mad cow disease or 
bovine spongiform encephalopathy (BSE) in cattle, chronic wasting disease (CWD) 
in deer and elk, and variant Creutzfeld-Jakob disease (vCJD) in humans. These 
diseases can lead to many animal deaths during an outbreak (Saunders et al., 
2009a). For these TSE diseases, the safe management of the prions remains of 
particular concern because of their ability to remain infective in the soil and 
through the feed chain (Russo et al., 2009; Saunders et al., 2009b).
Prions will be used throughout this document as an example of a pathogen 
that is difficult to inactivate. Prions are highly resistant to inactivation 
processes that are normally effective against bacterial and viral disease 
agents, such as chemical and thermal means, and ionizing, ultraviolet, and 
microwave irradiation processes. Incineration, if done properly, is effective at 
deactivating prions. Although a slow process, prion adsorption onto soil 
particles is strongly irreversible, and the prions can remain infectious through 
oral consumption (Saunders et al., 2009a; Saunders et al., 2009b). Prions can 
survive conventional wastewater treatment systems (Hinckley et al., 2008). 
Consequently, carcasses infected with prions cannot be buried, rendered, or 
placed near healthy livestock or livestock feed or water supplies.
BSE became a public health issue when it was connected to vCJD in humans 
(APHIS, 2013c). In cattle, BSE is a fatal disease of the brain that causes a 
spongy degeneration in the brain and spinal cord. BSE has a long incubation 
period, from 2 to 8 years. Once an animal develops symptoms, the animal’s 
condition deteriorates, and death usually occurs within the next 6 months.
III. Affected Environment 35
snip...
Potential risks to the public health from decomposing animal carcasses in 
landfills can influence an operator’s decision regarding whether to accept 
carcass material, even if the landfill is permitted to receive carcasses.
Some landfill owners refused to accept carcasses for burial during the 2001 
FMD outbreak in the United Kingdom (Nutsch and Spire, 2004), and in Wisconsin 
for the disposal of deer and elk carcasses stemming from an outbreak of 
CWD.
snip...
d. Spread of Disease
Scavengers feeding on disease-infected animal carcasses may spread diseases 
to other wildlife species, such as from feeding on deer carcasses infected with 
CWD (Jennelle et al., 2009). While the management of wild deer carcasses is not 
within the scope of this EIS, the management of captive deer raised as livestock 
could fall within the scope. Scavengers could spread CWD to animals within the 
family Cervidae, which are susceptible to CWD. Federally listed cervids that 
would be susceptible include Key deer (Odocoileus virginianus clavium), 
Columbian white-tailed deer (Odocoileus virginianus leucurus), and woodland 
caribou (Rangifer tarandus caribou). 
snip... 
Scrapie
“When required, cleaning and disinfection shall be conducted under the 
supervision of a State or APHIS representative…To clean dry surfaces, apply a 
2-percent chlorine bleach solution at room temperature….for 1 hour, or apply a 
1-molar solution of sodium hydroxide…at room temperature for at least 1 hour…” 9 
CFR § 54.7
Chronic Wasting Disease
“…all premises…and all other materials on any premises or conveyances used 
to house or transport such cervids must be cleaned and disinfected under the 
supervision of an APHIS employee or a State representative, using methods 
specified by the APHIS employee or a State representative.” 9 CFR § 55.4 
SNIP... 
Environmental Impact Statement; Animal Carcass ManagementDocket Folder 
Summary View all documents and comments in this Docket Docket ID: 
APHIS-2013-0044Agency: Animal and Plant Health Inspection Service (APHIS)Parent 
Agency: Department of Agriculture (USDA)Summary: 
We are announcing to the public that the Animal and Plant Health Inspection 
Service is making available a draft environmental impact statement (EIS) to 
examine the potential environmental effects of animal carcass management options 
used throughout the United States for review and comment. more... RIN: Impacts 
and Effects: CFR Citation: Priority: – View Fewer Docket Details UA and 
Regulatory Plan Informationopen glossary dialog Legal Deadline
Timetable
Docket Detailsopen glossary dialog Related RINs: None Related Dockets: None 
Category: Domestic Animal Health ProgramsKeyword(s): USDA, agriculture Type: 
Nonrulemaking Program: Veterinary Services Primary DocumentsView All (4) No 
documents available. Animal Carcass Management: Draft Environmental Impact 
Statement (EIS) Comment Now! Due Oct 20, 2015 11:59 PM ET Other Posted: 
08/14/2015ID: APHIS-2013-0044-0017 
 Environmental Impact Statements; Availability, etc.: Animal Carcass 
Management Comment Now! Comment Period Closed Jan 30, 2014 11:59 PM ET Notice 
Posted: 12/31/2013ID: APHIS-2013-0044-0009 
 Environmental Impact Statements; Availability, etc.: Animal Carcass 
Management Comment Now! Comment Period Closed Dec 26, 2013 11:59 PM ET Notice 
Posted: 10/25/2013ID: APHIS-2013-0044-0001 
--------------------------------------------------------------------------------
Supporting DocumentsView All (0) No documents available.
--------------------------------------------------------------------------------
CommentsView All (13) No comments posted. See attached file(s)” View 
Comment Submitter Name: Paulo, Terry AnnPosted: 02/03/2014ID: 
APHIS-2013-0044-0016 
 See attached file(s)” View Comment Submitter Name: Meisinger, 
JessicaPosted: 02/03/2014ID: APHIS-2013-0044-0015 
 Please see attached comment letter and supporting documents.” View Comment 
Submitter Name: Haldeman, DavidPosted: 01/29/2014ID: APHIS-2013-0044-0014 
 Hello, The Council for Agricultural Science and Technology has three 
excellent peer-reviewed research papers about this topic. The information will 
help...” View Comment Submitter Name: Gogerty, DanPosted: 01/14/2014ID: 
APHIS-2013-0044-0013 
 It would also be beneficial to include information or procedures for the 
humane euthanasia and disposal of large number of animals, in the event of a 
natural...” View Comment Submitter Name: Howard, AmyPosted: 01/08/2014ID: 
APHIS-2013-0044-0010 
Your comment was submitted successfully!. View all documents and comments 
in this Docket Success! You will now be commenting directly on: 
The Animal and Plant Health Inspection Service (APHIS) Notice: 
Environmental Impact Statements; Availability, etc.: Animal Carcass 
Management
For related information, Open Docket Folder Docket folder icon
.. 3.Your Receipt.3 Your Receipt 2 Your Preview 1 Your Information 
...publicly viewable Information entered will be viewable on Regulations.gov 
Agency Posting Guidelines: More infoView Commenter's Checklist (PDF) Alternate 
Ways to Comment. .Comment(Required) publicly viewable Greetings APHIS et al, and 
thank you kindly for allowing me to comment on Environmental Impact Statements; 
Availability, etc.: Animal Carcass Management [Docket No. APHIS-2013-0044]. 
SNIP... 
see my full text submission with source references in attachment...TSS 
Uploaded File(s)(Optional) No files uploaded [Docket No. APHIS-2013-0044] 
COMMENT SUBMISSION TERRY S. SINGELTARY SR..pdf: success 
end...November 2013...TSS 
 Singeltary Submission Environmental Impact Statements; Availability, etc.: 
Animal Carcass Management [Docket No. APHIS-2013-0044] 
Sunday, November 3, 2013 
Environmental Impact Statements; Availability, etc.: Animal Carcass 
Management [Docket No. APHIS-2013-0044] 
Monday, May 05, 2014 
*** Member Country details for listing OIE CWD 2013 against the criteria of 
Article 1.2.2., the Code Commission recommends consideration for listing 
***
PRION 2015 CONFERENCE FT. COLLINS CWD RISK FACTORS TO HUMANS 
*** LATE-BREAKING ABSTRACTS PRION 2015 CONFERENCE ***
O18
Zoonotic Potential of CWD Prions
Liuting Qing1, Ignazio Cali1,2, Jue Yuan1, Shenghai Huang3, Diane Kofskey1, 
Pierluigi Gambetti1, Wenquan Zou1, Qingzhong Kong1 1Case Western Reserve 
University, Cleveland, Ohio, USA, 2Second University of Naples, Naples, Italy, 
3Encore Health Resources, Houston, Texas, USA
Chronic wasting disease (CWD) is a widespread and expanding prion disease 
in free-ranging and captive cervid species in North America. The zoonotic 
potential of CWD prions is a serious public health concern. Current literature 
generated with in vitro methods and in vivo animal models (transgenic mice, 
macaques and squirrel monkeys) reports conflicting results. The susceptibility 
of human CNS and peripheral organs to CWD prions remains largely unresolved. In 
our earlier bioassay experiments using several humanized transgenic mouse lines, 
we detected protease-resistant PrPSc in the spleen of two out of 140 mice that 
were intracerebrally inoculated with natural CWD isolates, but PrPSc was not 
detected in the brain of the same mice. Secondary passages with such 
PrPSc-positive CWD-inoculated humanized mouse spleen tissues led to efficient 
prion transmission with clear clinical and pathological signs in both humanized 
and cervidized transgenic mice. Furthermore, a recent bioassay with natural CWD 
isolates in a new humanized transgenic mouse line led to clinical prion 
infection in 2 out of 20 mice. These results indicate that the CWD prion has the 
potential to infect human CNS and peripheral lymphoid tissues and that there 
might be asymptomatic human carriers of CWD infection. 
================== 
***These results indicate that the CWD prion has the potential to infect 
human CNS and peripheral lymphoid tissues and that there might be asymptomatic 
human carriers of CWD infection.*** 
================== 
P.105: RT-QuIC models trans-species prion transmission
Kristen Davenport, Davin Henderson, Candace Mathiason, and Edward Hoover 
Prion Research Center; Colorado State University; Fort Collins, CO USA
The propensity for trans-species prion transmission is related to the 
structural characteristics of the enciphering and heterologous PrP, but the 
exact mechanism remains mostly mysterious. Studies of the effects of primary or 
tertiary prion protein structures on trans-species prion transmission have 
relied primarily upon animal bioassays, making the influence of prion protein 
structure vs. host co-factors (e.g. cellular constituents, trafficking, and 
innate immune interactions) difficult to dissect. As an alternative strategy, we 
used real-time quakinginduced conversion (RT-QuIC) to investigate trans-species 
prion conversion.
To assess trans-species conversion in the RT-QuIC system, we compared 
chronic wasting disease (CWD) and bovine spongiform encephalopathy (BSE) prions, 
as well as feline CWD (fCWD) and feline spongiform encephalopathy (FSE). Each 
prion was seeded into each host recombinant PrP (full-length rPrP of 
white-tailed deer, bovine or feline). We demonstrated that fCWD is a more 
efficient seed for feline rPrP than for white-tailed deer rPrP, which suggests 
adaptation to the new host.
Conversely, FSE maintained sufficient BSE characteristics to more 
efficiently convert bovine rPrP than feline rPrP. Additionally, human rPrP was 
competent for conversion by CWD and fCWD. ***This insinuates that, at the level 
of protein:protein interactions, the barrier preventing transmission of CWD to 
humans is less robust than previously estimated.
================
***This insinuates that, at the level of protein:protein interactions, the 
barrier preventing transmission of CWD to humans is less robust than previously 
estimated.***
================ 
O.05: Transmission of prions to primates after extended silent incubation 
periods: Implications for BSE and scrapie risk assessment in human populations 
Emmanuel Comoy, Jacqueline Mikol, Val erie Durand, Sophie Luccantoni, 
Evelyne Correia, Nathalie Lescoutra, Capucine Dehen, and Jean-Philippe Deslys 
Atomic Energy Commission; Fontenay-aux-Roses, France 
Prion diseases (PD) are the unique neurodegenerative proteinopathies 
reputed to be transmissible under field conditions since decades. The 
transmission of Bovine Spongiform Encephalopathy (BSE) to humans evidenced that 
an animal PD might be zoonotic under appropriate conditions. Contrarily, in the 
absence of obvious (epidemiological or experimental) elements supporting a 
transmission or genetic predispositions, PD, like the other proteinopathies, are 
reputed to occur spontaneously (atpical animal prion strains, sporadic CJD 
summing 80% of human prion cases). Non-human primate models provided the first 
evidences supporting the transmissibiity of human prion strains and the zoonotic 
potential of BSE. Among them, cynomolgus macaques brought major information for 
BSE risk assessment for human health (Chen, 2014), according to their 
phylogenetic proximity to humans and extended lifetime. We used this model to 
assess the zoonotic potential of other animal PD from bovine, ovine and cervid 
origins even after very long silent incubation periods. *** We recently observed 
the direct transmission of a natural classical scrapie isolate to macaque after 
a 10-year silent incubation period, ***with features similar to some reported 
for human cases of sporadic CJD, albeit requiring fourfold longe incubation than 
BSE. Scrapie, as recently evoked in humanized mice (Cassard, 2014), ***is the 
third potentially zoonotic PD (with BSE and L-type BSE), ***thus questioning the 
origin of human sporadic cases. We will present an updated panorama of our 
different transmission studies and discuss the implications of such extended 
incubation periods on risk assessment of animal PD for human health.
===============
***thus questioning the origin of human sporadic cases...TSS
=============== 
Thursday, August 12, 2010 
Seven main threats for the future linked to prions 
***Also, a link is suspected between atypical BSE and some apparently 
sporadic cases of Creutzfeldt-Jakob disease in humans. These atypical BSE cases 
constitute an unforeseen first threat that could sharply modify the European 
approach to prion diseases. 
Second threat 
snip... 
Monday, October 10, 2011 
EFSA Journal 2011 The European Response to BSE: A Success Story 
snip... 
*** but the possibility that a small proportion of human cases so far 
classified as "sporadic" CJD are of zoonotic origin could not be excluded. 
Moreover, transmission experiments to non-human primates suggest that some TSE 
agents in addition to Classical BSE prions in cattle (namely L-type Atypical 
BSE, Classical BSE in sheep, transmissible mink encephalopathy (TME) and chronic 
wasting disease (CWD) agents) might have zoonotic potential. 
snip... 
***In addition, non-human primates are specifically susceptible for 
atypical BSE as demonstrated by an approximately 50% shortened incubation time 
for L-type BSE as compared to C-type. 
***Considering the current scientific information available, it cannot be 
assumed that these different BSE types pose the same human health risks as 
C-type BSE or that these risks are mitigated by the same protective measures. 
From: Terry S. Singeltary Sr. 
Sent: Saturday, November 15, 2014 9:29 PM 
To: Terry S. Singeltary Sr. 
Subject: THE EPIDEMIOLOGY OF CREUTZFELDT-JAKOB DISEASE R. G. WILL 
1984
THE EPIDEMIOLOGY OF CREUTZFELDT-JAKOB DISEASE 
R. G. WILL 
1984 
*** The association between venison eating and risk of CJD shows similar 
pattern, with regular venison eating associated with a 9 FOLD INCREASE IN RISK 
OF CJD (p = 0.04). (SEE LINK IN REPORT HERE...TSS) PLUS, THE CDC DID NOT PUT 
THIS WARNING OUT FOR THE WELL BEING OF THE DEER AND ELK ; 
snip... 
Evidence That Transmissible Mink Encephalopathy Results from Feeding 
Infected Cattle 
Over the next 8-10 weeks, approximately 40% of all the adult mink on the 
farm died from TME. 
snip... 
The rancher was a ''dead stock'' feeder using mostly (>95%) downer or 
dead dairy cattle... 
In Confidence - Perceptions of unconventional slow virus diseases of 
animals in the USA - APRIL-MAY 1989 - G A H Wells 
3. Prof. A. Robertson gave a brief account of BSE. The US approach was to 
accord it a very low profile indeed. Dr. A Thiermann showed the picture in the 
''Independent'' with cattle being incinerated and thought this was a fanatical 
incident to be avoided in the US at all costs. ... 
human cwd will NOT look like nvCJD. in fact, see ; 
*** These results would seem to suggest that CWD does indeed have zoonotic 
potential, at least as judged by the compatibility of CWD prions and their human 
PrPC target. Furthermore, extrapolation from this simple in vitro assay suggests 
that if zoonotic CWD occurred, it would most likely effect those of the PRNP 
codon 129-MM genotype and that the PrPres type would be similar to that found in 
the most common subtype of sCJD (MM1).*** 
Transmission of scrapie prions to primate after an extended silent 
incubation period 
Emmanuel E. Comoy1 , Jacqueline Mikol1 , Sophie Luccantoni-Freire1 , 
Evelyne Correia1 , Nathalie Lescoutra-Etchegaray1 , Valérie Durand1 , Capucine 
Dehen1 , Olivier Andreoletti2 , Cristina Casalone3 , Juergen A. Richt4 n1 , 
Justin J. Greenlee4 , Thierry Baron5 , Sylvie L. Benestad6 , Paul Brown1 […] 
& Jean-Philippe Deslys1 - Show fewer authors Scientific Reports 5, Article 
number: 11573 (2015) doi:10.1038/srep11573 Download Citation 
Epidemiology | Neurological manifestations | Prion diseases Received: 16 
February 2015 Accepted: 28 May 2015 Published online: 30 June 2015 ABSTRACT 
Classical bovine spongiform encephalopathy (c-BSE) is the only animal prion 
disease reputed to be zoonotic, causing variant Creutzfeldt-Jakob disease (vCJD) 
in humans and having guided protective measures for animal and human health 
against animal prion diseases. Recently, partial transmissions to humanized mice 
showed that the zoonotic potential of scrapie might be similar to c-BSE. We here 
report the direct transmission of a natural classical scrapie isolate to 
cynomolgus macaque, a highly relevant model for human prion diseases, after a 
10-year silent incubation period, with features similar to those reported for 
human cases of sporadic CJD. Scrapie is thus actually transmissible to primates 
with incubation periods compatible with their life expectancy, although fourfold 
longer than BSE. Long-term experimental transmission studies are necessary to 
better assess the zoonotic potential of other prion diseases with high 
prevalence, notably Chronic Wasting Disease of deer and elk and atypical/Nor98 
scrapie. 
snip... 
Discussion 
We describe the transmission of spongiform encephalopathy in a non-human 
primate inoculated 10 years earlier with a strain of sheep c-scrapie. Because of 
this extended incubation period in a facility in which other prion diseases are 
under study, we are obliged to consider two alternative possibilities that might 
explain its occurrence. We first considered the possibility of a sporadic origin 
(like CJD in humans). Such an event is extremely improbable because the 
inoculated animal was 14 years old when the clinical signs appeared, i.e. about 
40% through the expected natural lifetime of this species, compared to a peak 
age incidence of 60–65 years in human sporadic CJD, or about 80% through their 
expected lifetimes. Moreover, sporadic disease has never been observed in 
breeding colonies or primate research laboratories, most notably among hundreds 
of animals over several decades of study at the National Institutes of Health25, 
and in nearly twenty older animals continuously housed in our own 
facility.
The second possibility is a laboratory cross-contamination. Three facts 
make this possibility equally unlikely. First, handling of specimens in our 
laboratory is performed with fastidious attention to the avoidance of any such 
cross-contamination. Second, no laboratory cross-contamination has ever been 
documented in other primate laboratories, including the NIH, even between 
infected and uninfected animals housed in the same or adjacent cages with daily 
intimate contact (P. Brown, personal communication). Third, the cerebral lesion 
profile is different from all the other prion diseases we have studied in this 
model19, with a correlation between cerebellar lesions (massive spongiform 
change of Purkinje cells, intense PrPres staining and reactive gliosis26) and 
ataxia. The iron deposits present in the globus pallidus are a non specific 
finding that have been reported previously in neurodegenerative diseases and 
aging27. Conversely, the thalamic lesion was reminiscent of a metabolic disease 
due to thiamine deficiency28 but blood thiamine levels were within normal limits 
(data not shown). The preferential distribution of spongiform change in cortex 
associated with a limited distribution in the brainstem is reminiscent of the 
lesion profile in MM2c and VV1 sCJD patients29, but interspecies comparison of 
lesion profiles should be interpreted with caution. It is of note that the same 
classical scrapie isolate induced TSE in C57Bl/6 mice with similar incubation 
periods and lesional profiles as a sample derived from a MM1 sCJD 
patient30.
We are therefore confident that the illness in this cynomolgus macaque 
represents a true transmission of a sheep c-scrapie isolate directly to an 
old-world monkey, which taxonomically resides in the primate subdivision 
(parvorder of catarrhini) that includes humans. With an homology of its PrP 
protein with humans of 96.4%31, cynomolgus macaque constitutes a highly relevant 
model for assessing zoonotic risk of prion diseases. Since our initial aim was 
to show the absence of transmission of scrapie to macaques in the worst-case 
scenario, we obtained materials from a flock of naturally-infected sheep, 
affecting animals with different genotypes32. This c-scrapie isolate exhibited 
complete transmission in ARQ/ARQ sheep (332 ± 56 days) and Tg338 transgenic mice 
expressing ovine VRQ/VRQ prion protein (220 ± 5 days) (O. Andreoletti, personal 
communication). From the standpoint of zoonotic risk, it is important to note 
that sheep with c-scrapie (including the isolate used in our study) have 
demonstrable infectivity throughout their lymphoreticular system early in the 
incubation period of the disease (3 months-old for all the lymphoid organs, and 
as early as 2 months-old in gut-associated lymph nodes)33. In addition, scrapie 
infectivity has been identified in blood34, milk35 and skeletal muscle36 from 
asymptomatic but scrapie infected small ruminants which implies a potential 
dietary exposure for consumers.
Two earlier studies have reported the occurrence of clinical TSE in 
cynomolgus macaques after exposures to scrapie isolates. In the first study, the 
“Compton” scrapie isolate (derived from an English sheep) and serially 
propagated for 9 passages in goats did not transmit TSE in cynomolgus macaque, 
rhesus macaque or chimpanzee within 7 years following intracerebral challenge1; 
conversely, after 8 supplementary passages in conventional mice, this “Compton” 
isolate induced TSE in a cynomolgus macaque 5 years after intracerebral 
challenge, but rhesus macaques and chimpanzee remained asymptomatic 8.5 years 
post-exposure8. However, multiple successive passages that are classically used 
to select laboratory-adapted prion strains can significantly modify the initial 
properties of a scrapie isolate, thus questioning the relevance of zoonotic 
potential for the initial sheep-derived isolate. The same isolate had also 
induced disease into squirrel monkeys (new-world monkey)9. A second historical 
observation reported that a cynomolgus macaque developed TSE 6 years 
post-inoculation with brain homogenate from a scrapie-infected Suffolk ewe 
(derived from USA), whereas a rhesus macaque and a chimpanzee exposed to the 
same inoculum remained healthy 9 years post-exposure1. This inoculum also 
induced TSE in squirrel monkeys after 4 passages in mice. Other scrapie 
transmission attempts in macaque failed but had more shorter periods of 
observation in comparison to the current study. Further, it is possible that 
there are differences in the zoonotic potential of different scrapie 
strains.
The most striking observation in our study is the extended incubation 
period of scrapie in the macaque model, which has several implications. Firstly, 
our observations constitute experimental evidence in favor of the zoonotic 
potential of c-scrapie, at least for this isolate that has been extensively 
studied32,33,34,35,36. The cross-species zoonotic ability of this isolate should 
be confirmed by performing duplicate intracerebral exposures and assessing the 
transmissibility by the oral route (a successful transmission of prion strains 
through the intracerebral route may not necessarily indicate the potential for 
oral transmission37). However, such confirmatory experiments may require more 
than one decade, which is hardly compatible with current general management and 
support of scientific projects; thus this study should be rather considered as a 
case report.
Secondly, transmission of c-BSE to primates occurred within 8 years post 
exposure for the lowest doses able to transmit the disease (the survival period 
after inoculation is inversely proportional to the initial amount of infectious 
inoculum). The occurrence of scrapie 10 years after exposure to a high dose (25 
mg) of scrapie-infected sheep brain suggests that the macaque has a higher 
species barrier for sheep c-scrapie than c-BSE, although it is notable that 
previous studies based on in vitro conversion of PrP suggested that BSE and 
scrapie prions would have a similar conversion potential for human PrP38.
Thirdly, prion diseases typically have longer incubation periods after oral 
exposure than after intracerebral inoculations: since humans can develop Kuru 47 
years after oral exposure39, an incubation time of several decades after oral 
exposure to scrapie would therefore be expected, leading the disease to occur in 
older adults, i.e. the peak age for cases considered to be sporadic disease, and 
making a distinction between scrapie-associated and truly sporadic disease 
extremely difficult to appreciate.
Fourthly, epidemiologic evidence is necessary to confirm the zoonotic 
potential of an animal disease suggested by experimental studies. A relatively 
short incubation period and a peculiar epidemiological situation (e.g., all the 
first vCJD cases occurring in the country with the most important ongoing c-BSE 
epizootic) led to a high degree of suspicion that c-BSE was the cause of vCJD. 
Sporadic CJD are considered spontaneous diseases with an almost stable and 
constant worldwide prevalence (0.5–2 cases per million inhabitants per year), 
and previous epidemiological studies were unable to draw a link between sCJD and 
classical scrapie6,7,40,41, even though external causes were hypothesized to 
explain the occurrence of some sCJD clusters42,43,44. However, extended 
incubation periods exceeding several decades would impair the predictive values 
of epidemiological surveillance for prion diseases, already weakened by a 
limited prevalence of prion diseases and the multiplicity of isolates gathered 
under the phenotypes of “scrapie” and “sporadic CJD”.
Fifthly, considering this 10 year-long incubation period, together with 
both laboratory and epidemiological evidence of decade or longer intervals 
between infection and clinical onset of disease, no premature conclusions should 
be drawn from negative transmission studies in cynomolgus macaques with less 
than a decade of observation, as in the aforementioned historical transmission 
studies of scrapie to primates1,8,9. Our observations and those of others45,46 
to date are unable to provide definitive evidence regarding the zoonotic 
potential of CWD, atypical/Nor98 scrapie or H-type BSE. The extended incubation 
period of the scrapie-affected macaque in the current study also underscores the 
limitations of rodent models expressing human PrP for assessing the zoonotic 
potential of some prion diseases since their lifespan remains limited to 
approximately two years21,47,48. This point is illustrated by the fact that the 
recently reported transmission of scrapie to humanized mice was not associated 
with clinical signs for up to 750 days and occurred in an extreme minority of 
mice with only a marginal increase in attack rate upon second passage13. The low 
attack rate in these studies is certainly linked to the limited lifespan of mice 
compared to the very long periods of observation necessary to demonstrate the 
development of scrapie. Alternatively, one could estimate that a successful 
second passage is the result of strain adaptation to the species barrier, thus 
poorly relevant of the real zoonotic potential of the original scrapie isolate 
of sheep origin49. The development of scrapie in this primate after an 
incubation period compatible with its lifespan complements the study conducted 
in transgenic (humanized) mice; taken together these studies suggest that some 
isolates of sheep scrapie can promote misfolding of the human prion protein and 
that scrapie can develop within the lifespan of some primate species.
In addition to previous studies on scrapie transmission to primate1,8,9 and 
the recently published study on transgenic humanized mice13, our results 
constitute new evidence for recommending that the potential risk of scrapie for 
human health should not be dismissed. Indeed, human PrP transgenic mice and 
primates are the most relevant models for investigating the human transmission 
barrier. To what extent such models are informative for measuring the zoonotic 
potential of an animal TSE under field exposure conditions is unknown. During 
the past decades, many protective measures have been successfully implemented to 
protect cattle from the spread of c-BSE, and some of these measures have been 
extended to sheep and goats to protect from scrapie according to the principle 
of precaution. Since cases of c-BSE have greatly reduced in number, those 
protective measures are currently being challenged and relaxed in the absence of 
other known zoonotic animal prion disease. We recommend that risk managers 
should be aware of the long term potential risk to human health of at least 
certain scrapie isolates, notably for lymphotropic strains like the classical 
scrapie strain used in the current study. Relatively high amounts of infectivity 
in peripheral lymphoid organs in animals infected with these strains could lead 
to contamination of food products produced for human consumption. Efforts should 
also be maintained to further assess the zoonotic potential of other animal 
prion strains in long-term studies, notably lymphotropic strains with high 
prevalence like CWD, which is spreading across North America, and atypical/Nor98 
scrapie (Nor98)50 that was first detected in the past two decades and now 
represents approximately half of all reported cases of prion diseases in small 
ruminants worldwide, including territories previously considered as scrapie 
free. Even if the prevailing view is that sporadic CJD is due to the spontaneous 
formation of CJD prions, it remains possible that its apparent sporadic nature 
may, at least in part, result from our limited capacity to identify an 
environmental origin. 
 98 | Veterinary Record | January 24, 2015 
EDITORIAL 
Scrapie: a particularly persistent pathogen 
Cristina Acín 
Resistant prions in the environment have been the sword of Damocles for 
scrapie control and eradication. Attempts to establish which physical and 
chemical agents could be applied to inactivate or moderate scrapie infectivity 
were initiated in the 1960s and 1970s,with the first study of this type focusing 
on the effect of heat treatment in reducing prion infectivity (Hunter and 
Millson 1964). Nowadays, most of the chemical procedures that aim to inactivate 
the prion protein are based on the method developed by Kimberlin and 
collaborators (1983). This procedure consists of treatment with 20,000 parts per 
million free chlorine solution, for a minimum of one hour, of all surfaces that 
need to be sterilised (in laboratories, lambing pens, slaughterhouses, and so 
on). Despite this, veterinarians and farmers may still ask a range of questions, 
such as ‘Is there an official procedure published somewhere?’ and ‘Is there an 
international organisation which recommends and defines the exact method of 
scrapie decontamination that must be applied?’ 
From a European perspective, it is difficult to find a treatment that could 
be applied, especially in relation to the disinfection of surfaces in lambing 
pens of affected flocks. A 999/2001 EU regulation on controlling spongiform 
encephalopathies (European Parliament and Council 2001) did not specify a 
particular decontamination measure to be used when an outbreak of scrapie is 
diagnosed. There is only a brief recommendation in Annex VII concerning the 
control and eradication of transmissible spongiform encephalopathies (TSE s). 
Chapter B of the regulation explains the measures that must be applied if 
new caprine animals are to be introduced to a holding where a scrapie outbreak 
has previously been diagnosed. In that case, the statement indicates that 
caprine animals can be introduced ‘provided that a cleaning and disinfection of 
all animal housing on the premises has been carried out following destocking’. 
Issues around cleaning and disinfection are common in prion prevention 
recommendations, but relevant authorities, veterinarians and farmers may have 
difficulties in finding the specific protocol which applies. The European Food 
and Safety Authority (EFSA ) published a detailed report about the efficacy of 
certain biocides, such as sodium hydroxide, sodium hypochlorite, guanidine and 
even a formulation of copper or iron metal ions in combination with hydrogen 
peroxide, against prions (EFSA 2009). The report was based on scientific 
evidence (Fichet and others 2004, Lemmer and others 2004, Gao and others 2006, 
Solassol and others 2006) but unfortunately the decontamination measures were 
not assessed under outbreak conditions. 
The EFSA Panel on Biological Hazards recently published its conclusions on 
the scrapie situation in the EU after 10 years of monitoring and control of the 
disease in sheep and goats (EFSA 2014), and one of the most interesting findings 
was the Icelandic experience regarding the effect of disinfection in scrapie 
control. The Icelandic plan consisted of: culling scrapie-affected sheep or the 
whole flock in newly diagnosed outbreaks; deep cleaning and disinfection of 
stables, sheds, barns and equipment with high pressure washing followed by 
cleaning with 500 parts per million of hypochlorite; drying and treatment with 
300 ppm of iodophor; and restocking was not permitted for at least two years. 
Even when all of these measures were implemented, scrapie recurred on several 
farms, indicating that the infectious agent survived for years in the 
environment, even as many as 16 years after restocking (Georgsson and others 
2006). 
In the rest of the countries considered in the EFSA (2014) report, 
recommendations for disinfection measures were not specifically defined at the 
government level. In the report, the only recommendation that is made for sheep 
is repopulation with sheep with scrapie-resistant genotypes. This reduces the 
risk of scrapie recurrence but it is difficult to know its effect on the 
infection. 
Until the EFSA was established (in May 2003), scientific opinions about TSE 
s were provided by the Scientific Steering Committee (SSC) of the EC, whose 
advice regarding inactivation procedures focused on treating animal waste at 
high temperatures (150°C for three hours) and high pressure alkaline hydrolysis 
(SSC 2003). At the same time, the TSE Risk Management Subgroup of the Advisory 
Committee on Dangerous Pathogens (ACDP) in the UK published guidance on safe 
working and the prevention of TSE infection. Annex C of the ACDP report 
established that sodium hypochlorite was considered to be effective, but only if 
20,000 ppm of available chlorine was present for at least one hour, which has 
practical limitations such as the release of chlorine gas, corrosion, 
incompatibility with formaldehyde, alcohols and acids, rapid inactivation of its 
active chemicals and the stability of dilutions (ACDP 2009). 
In an international context, the World Organisation for Animal Health (OIE) 
does not recommend a specific disinfection protocol for prion agents in its 
Terrestrial Code or Manual. Chapter 4.13 of the Terrestrial Code, General 
recommendations on disinfection and disinsection (OIE 2014), focuses on 
foot-and-mouth disease virus, mycobacteria and Bacillus anthracis, but not on 
prion disinfection. Nevertheless, the last update published by the OIE on bovine 
spongiform encephalopathy (OIE 2012) indicates that few effective 
decontamination techniques are available to inactivate the agent on surfaces, 
and recommends the removal of all organic material and the use of sodium 
hydroxide, or a sodium hypochlorite solution containing 2 per cent available 
chlorine, for more than one hour at 20ºC. 
The World Health Organization outlines guidelines for the control of TSE s, 
and also emphasises the importance of mechanically cleaning surfaces before 
disinfection with sodium hydroxide or sodium hypochlorite for one hour (WHO 
1999). 
Finally, the relevant agencies in both Canada and the USA suggest that the 
best treatments for surfaces potentially contaminated with prions are sodium 
hydroxide or sodium hypochlorite at 20,000 ppm. This is a 2 per cent solution, 
while most commercial household bleaches contain 5.25 per cent sodium 
hypochlorite. It is therefore recommended to dilute one part 5.25 per cent 
bleach with 1.5 parts water (CDC 2009, Canadian Food Inspection Agency 2013). 
So what should we do about disinfection against prions? First, it is 
suggested that a single protocol be created by international authorities to 
homogenise inactivation procedures and enable their application in all 
scrapie-affected countries. Sodium hypochlorite with 20,000 ppm of available 
chlorine seems to be the procedure used in most countries, as noted in a paper 
summarised on p 99 of this issue of Veterinary Record (Hawkins and others 2015). 
But are we totally sure of its effectiveness as a preventive measure in a 
scrapie outbreak? Would an in-depth study of the recurrence of scrapie disease 
be needed? 
What we can conclude is that, if we want to fight prion diseases, and 
specifically classical scrapie, we must focus on the accuracy of diagnosis, 
monitoring and surveillance; appropriate animal identification and control of 
movements; and, in the end, have homogeneous and suitable protocols to 
decontaminate and disinfect lambing barns, sheds and equipment available to 
veterinarians and farmers. Finally, further investigations into the resistance 
of prion proteins in the diversity of environmental surfaces are required. 
References 
snip... 
98 | Veterinary Record | January 24, 2015 
Persistence of ovine scrapie infectivity in a farm environment following 
cleaning and decontamination 
Steve A. C. Hawkins, MIBiol, Pathology Department1, Hugh A. Simmons, BVSc 
MRCVS, MBA, MA Animal Services Unit1, Kevin C. Gough, BSc, PhD2 and Ben C. 
Maddison, BSc, PhD3 + Author Affiliations 
1Animal and Plant Health Agency, Woodham Lane, New Haw, Addlestone, Surrey 
KT15 3NB, UK 2School of Veterinary Medicine and Science, The University of 
Nottingham, Sutton Bonington, Loughborough, Leicestershire LE12 5RD, UK 3ADAS 
UK, School of Veterinary Medicine and Science, The University of Nottingham, 
Sutton Bonington, Loughborough, Leicestershire LE12 5RD, UK E-mail for 
correspondence: ben.maddison@adas.co.uk Abstract Scrapie of sheep/goats and 
chronic wasting disease of deer/elk are contagious prion diseases where 
environmental reservoirs are directly implicated in the transmission of disease. 
In this study, the effectiveness of recommended scrapie farm decontamination 
regimens was evaluated by a sheep bioassay using buildings naturally 
contaminated with scrapie. Pens within a farm building were treated with either 
20,000 parts per million free chorine solution for one hour or were treated with 
the same but were followed by painting and full re-galvanisation or replacement 
of metalwork within the pen. Scrapie susceptible lambs of the PRNP genotype 
VRQ/VRQ were reared within these pens and their scrapie status was monitored by 
recto-anal mucosa-associated lymphoid tissue. All animals became infected over 
an 18-month period, even in the pen that had been subject to the most stringent 
decontamination process. These data suggest that recommended current guidelines 
for the decontamination of farm buildings following outbreaks of scrapie do 
little to reduce the titre of infectious scrapie material and that environmental 
recontamination could also be an issue associated with these premises. 
SNIP... 
Discussion 
Thorough pressure washing of a pen had no effect on the amount of 
bioavailable scrapie infectivity (pen B). The routine removal of prions from 
surfaces within a laboratory setting is treatment for a minimum of one hour with 
20,000 ppm free chlorine, a method originally based on the use of brain 
macerates from infected rodents to evaluate the effectiveness of decontamination 
(Kimberlin and others 1983). Further studies have also investigated the 
effectiveness of hypochlorite disinfection of metal surfaces to simulate the 
decontamination of surgical devices within a hospital setting. Such treatments 
with hypochlorite solution were able to reduce infectivity by 5.5 logs to lower 
than the sensitivity of the bioassay used (Lemmer and others 2004). Analogous 
treatment of the pen surfaces did not effectively remove the levels of scrapie 
infectivity over that of the control pens, indicating that this method of 
decontamination is not effective within a farm setting. This may be due to the 
high level of biological matrix that is present upon surfaces within the farm 
environment, which may reduce the amount of free chlorine available to 
inactivate any infectious prion. Remarkably 1/5 sheep introduced into pen D had 
also became scrapie positive within nine months, with all animals in this pen 
being RAMALT positive by 18 months of age. Pen D was no further away from the 
control pen (pen A) than any of the other pens within this barn. Localised hot 
spots of infectivity may be present within scrapie-contaminated environments, 
but it is unlikely that pen D area had an amount of scrapie contamination that 
was significantly different than the other areas within this building. 
Similarly, there were no differences in how the biosecurity of pen D was 
maintained, or how this pen was ventilated compared with the other pens. This 
observation, perhaps, indicates the slower kinetics of disease uptake within 
this pen and is consistent with a more thorough prion removal and 
recontamination. These observations may also account for the presence of 
inadvertent scrapie cases within other studies, where despite stringent 
biosecurity, control animals have become scrapie positive during challenge 
studies using barns that also housed scrapie-affected animals (Ryder and others 
2009). The bioassay data indicate that the exposure of the sheep to a farm 
environment after decontamination efforts thought to be effective in removing 
scrapie is sufficient for the animals to become infected with scrapie. The main 
exposure routes within this scenario are likely to be via the oral route, during 
feeding and drinking, and respiratory and conjunctival routes. It has been 
demonstrated that scrapie infectivity can be efficiently transmitted via the 
nasal route in sheep (Hamir and others 2008), as is the case for CWD in both 
murine models and in white-tailed deer (Denkers and others 2010, 2013). 
Recently, it has also been demonstrated that CWD prions presented as dust when 
bound to the soil mineral montmorillonite can be infectious via the nasal route 
(Nichols and others 2013). When considering pens C and D, the actual source of 
the infectious agent in the pens is not known, it is possible that biologically 
relevant levels of prion survive on surfaces during the decontamination regimen 
(pen C). With the use of galvanising and painting (pen D) covering and sealing 
the surface of the pen, it is possible that scrapie material recontaminated the 
pens by the movement of infectious prions contained within dusts originating 
from other parts of the barn that were not decontaminated or from other areas of 
the farm. 
Given that scrapie prions are widespread on the surfaces of affected farms 
(Maddison and others 2010a), irrespective of the source of the infectious prions 
in the pens, this study clearly highlights the difficulties that are faced with 
the effective removal of environmentally associated scrapie infectivity. This is 
likely to be paralleled in CWD which shows strong similarities to scrapie in 
terms of both the dissemination of prions into the environment and the facile 
mode of disease transmission. These data further contribute to the understanding 
that prion diseases can be highly transmissible between susceptible individuals 
not just by direct contact but through highly stable environmental reservoirs 
that are refractory to decontamination. 
The presence of these environmentally associated prions in farm buildings 
make the control of these diseases a considerable challenge, especially in 
animal species such as goats where there is lack of genetic resistance to 
scrapie and, therefore, no scope to re-stock farms with animals that are 
resistant to scrapie. 
Scrapie Sheep Goats Transmissible spongiform encephalopathies (TSE) 
Accepted October 12, 2014. Published Online First 31 October 2014 
PPo3-22: 
Detection of Environmentally Associated PrPSc on a Farm with Endemic 
Scrapie 
Ben C. Maddison,1 Claire A. Baker,1 Helen C. Rees,1 Linda A. Terry,2 Leigh 
Thorne,2 Susan J. Belworthy2 and Kevin C. Gough3 1ADAS-UK LTD; Department of 
Biology; University of Leicester; Leicester, UK; 2Veterinary Laboratories 
Agency; Surry, KT UK; 3Department of Veterinary Medicine and Science; University 
of Nottingham; Sutton Bonington, Loughborough UK 
Key words: scrapie, evironmental persistence, sPMCA 
Ovine scrapie shows considerable horizontal transmission, yet the routes of 
transmission and specifically the role of fomites in transmission remain poorly 
defined. Here we present biochemical data demonstrating that on a 
scrapie-affected sheep farm, scrapie prion contamination is widespread. It was 
anticipated at the outset that if prions contaminate the environment that they 
would be there at extremely low levels, as such the most sensitive method 
available for the detection of PrPSc, serial Protein Misfolding Cyclic 
Amplification (sPMCA), was used in this study. We investigated the distribution 
of environmental scrapie prions by applying ovine sPMCA to samples taken from a 
range of surfaces that were accessible to animals and could be collected by use 
of a wetted foam swab. Prion was amplified by sPMCA from a number of these 
environmental swab samples including those taken from metal, plastic and wooden 
surfaces, both in the indoor and outdoor environment. At the time of sampling 
there had been no sheep contact with these areas for at least 20 days prior to 
sampling indicating that prions persist for at least this duration in the 
environment. These data implicate inanimate objects as environmental reservoirs 
of prion infectivity which are likely to contribute to disease transmission. 
*** Approximately 4,200 fawns, defined as deer under 1 year of age, were 
sampled from the eradication zone over the last year. The majority of fawns 
sampled were between the ages of 5 to 9 months, though some were as young as 1 
month. Two of the six fawns with CWD detected were 5 to 6 months old. All six of 
the positive fawns were taken from the core area of the CWD eradication zone 
where the highest numbers of positive deer have been identified. 
"This is the first intensive sampling for CWD in fawns anywhere," said Dr. 
Julie Langenberg, Department of Natural Resources wildlife veterinarian, "and we 
are trying to learn as much as we can from these data". 
Tuesday, July 21, 2015 
Texas CWD Medina County Herd Investigation Update July 16, 2015 
• 66 Texas sites, 2 Mexico sites 
Wednesday, July 22, 2015 
Texas Certified Chronic Wasting Disease CWD Sample Collector, like the Wolf 
Guarding the Henhouse 
Thursday, July 23, 2015 
*** Chronic Wasting Disease (CWD) 101 Drs. Walter Cook & Donald S. 
Davis 
Sunday, July 26, 2015 
*** TEXAS IN MELT DOWN MODE OVER CAPTIVE CWD AND THEY ARE PUTTING LIPSTICK 
ON THAT PIG AND TAKING HER TO THE DANCE LIKE MAD COW DISEASE *** 
Tuesday, July 28, 2015 
TEXAS Kills 35 Deer at Medina County Ranch (Texas Captive CWD) 
Tuesday, August 11, 2015 
Why Has the Federal Government Cut Funding for Chronic Wasting Disease 
Research? 
http://chronic-wasting-disease.blogspot.com/2015/08/why-has-federal-government-cut-funding.html 
Tuesday, August 11, 2015 
Wisconsin doing what it does best, procrastinating about CWD yet again 
thanks to Governor Walker 
IF the state of Texas does not get serious real fast with CWD, and test all 
those deer, that 5 year plan is a ticking time bomb waiting to happen. 
all cervid tested after slaughter, and test results must be released to the 
public. 
the tse prion aka mad cow type disease is not your normal pathogen. 
The TSE prion disease survives ashing to 600 degrees celsius, that’s around 
1112 degrees farenheit. 
you cannot cook the TSE prion disease out of meat. 
you can take the ash and mix it with saline and inject that ash into a 
mouse, and the mouse will go down with TSE. 
Prion Infected Meat-and-Bone Meal Is Still Infectious after Biodiesel 
Production as well. 
the TSE prion agent also survives Simulated Wastewater Treatment Processes. 
IN fact, you should also know that the TSE Prion agent will survive in the 
environment for years, if not decades. 
you can bury it and it will not go away. 
The TSE agent is capable of infected your water table i.e. Detection of 
protease-resistant cervid prion protein in water from a CWD-endemic area. 
it’s not your ordinary pathogen you can just cook it out and be done with. 
that’s what’s so worrisome about Iatrogenic mode of transmission, a simple 
autoclave will not kill this TSE prion agent. 
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 
*** Infectious agent of sheep scrapie may persist in the environment for at 
least 16 years*** 
Gudmundur Georgsson1, Sigurdur Sigurdarson2 and Paul Brown3 
Longitudinal Detection of Prion Shedding in Saliva and Urine by 
CWD-Infected Deer by RT-QuIC 
Davin M. Henderson1, Nathaniel D. Denkers1, Clare E. Hoover1, Nina 
Garbino1, Candace K. Mathiason1 and Edward A. Hoover1# + Author Affiliations 
1Prion Research Center, Department of Microbiology, Immunology, and 
Pathology, College of Veterinary Medicine and Biomedical Sciences, Colorado 
State University, Fort Collins, CO 80523 
ABSTRACT Chronic Wasting Disease (CWD) is an emergent, rapidly spreading 
prion disease of cervids. Shedding of infectious prions in saliva and urine is 
thought to be an important factor in CWD transmission. To help elucidate this 
issue, we applied an in vitro amplification assay to determine the onset, 
duration, and magnitude of prion shedding in longitudinally collected saliva and 
urine samples from CWD-exposed white-tailed deer. We detected prion shedding as 
early as 3 months after CWD exposure and sustained shedding throughout the 
disease course. We estimated that a 50% lethal dose (LD50) for cervidized 
transgenic mice would be contained in 1 ml of infected deer saliva or 10 ml or 
urine. Given the average course of infection and daily production of these body 
fluids, an infected deer would shed thousands of prion infectious doses over the 
course of CWD infection. The direct and indirect environmental impact of this 
magnitude of prion shedding for cervid and non-cervid species is surely 
significant. 
Importance: Chronic wasting disease (CWD) is an emerging and uniformly 
fatal prion disease affecting free ranging deer and elk and now recognized in 22 
United States and 2 C anadian Provinces. It is unique among prion diseases in 
that it is transmitted naturally though wild populations. A major hypothesis for 
CWD's florid spread is that prions are shed in excreta and transmitted via 
direct or indirect environmental contact. Here we use a rapid in vitro assay to 
show that infectious doses of CWD prions are in fact shed throughout the 
multi-year disease course in deer. This finding is an important advance in 
assessing the risks posed by shed CWD prions to animals as well as humans. 
FOOTNOTES 
↵#To whom correspondence should be addressed: Edward A. Hoover, Prion 
Research Center, Department of Microbiology, Immunology and Pathology, Colorado 
State University, Fort Collins, Colorado, US Email: edward.hoover@colostate.edu 
Friday, December 14, 2012 
DEFRA U.K. What is the risk of Chronic Wasting Disease CWD being introduced 
into Great Britain? A Qualitative Risk Assessment October 2012 
snip... 
In the USA, under the Food and Drug Administration’s BSE Feed Regulation 
(21 CFR 589.2000) most material (exceptions include milk, tallow, and gelatin) 
from deer and elk is prohibited for use in feed for ruminant animals. With 
regards to feed for non-ruminant animals, under FDA law, CWD positive deer may 
not be used for any animal feed or feed ingredients. For elk and deer considered 
at high risk for CWD, the FDA recommends that these animals do not enter the 
animal feed system. However, this recommendation is guidance and not a 
requirement by law. 
Animals considered at high risk for CWD include: 
1) animals from areas declared to be endemic for CWD and/or to be CWD 
eradication zones and 
2) deer and elk that at some time during the 60-month period prior to 
slaughter were in a captive herd that contained a CWD-positive animal. 
Therefore, in the USA, materials from cervids other than CWD positive 
animals may be used in animal feed and feed ingredients for non-ruminants. 
The amount of animal PAP that is of deer and/or elk origin imported from 
the USA to GB can not be determined, however, as it is not specified in TRACES. 
It may constitute a small percentage of the 8412 kilos of non-fish origin 
processed animal proteins that were imported from US into GB in 2011. 
Overall, therefore, it is considered there is a __greater than negligible 
risk___ that (nonruminant) animal feed and pet food containing deer and/or elk 
protein is imported into GB. 
There is uncertainty associated with this estimate given the lack of data 
on the amount of deer and/or elk protein possibly being imported in these 
products. 
snip... 
36% in 2007 (Almberg et al., 2011). In such areas, population declines of 
deer of up to 30 to 50% have been observed (Almberg et al., 2011). In areas of 
Colorado, the prevalence can be as high as 30% (EFSA, 2011). The clinical signs 
of CWD in affected adults are weight loss and behavioural changes that can span 
weeks or months (Williams, 2005). In addition, signs might include excessive 
salivation, behavioural alterations including a fixed stare and changes in 
interaction with other animals in the herd, and an altered stance (Williams, 
2005). These signs are indistinguishable from cervids experimentally infected 
with bovine spongiform encephalopathy (BSE). Given this, if CWD was to be 
introduced into countries with BSE such as GB, for example, infected deer 
populations would need to be tested to differentiate if they were infected with 
CWD or BSE to minimise the risk of BSE entering the human food-chain via 
affected venison. 
snip... 
The rate of transmission of CWD has been reported to be as high as 30% and 
can approach 100% among captive animals in endemic areas (Safar et al., 2008). 
snip... 
In summary, in endemic areas, there is a medium probability that the soil 
and surrounding environment is contaminated with CWD prions and in a 
bioavailable form. In rural areas where CWD has not been reported and deer are 
present, there is a greater than negligible risk the soil is contaminated with 
CWD prion. 
snip... 
In summary, given the volume of tourists, hunters and servicemen moving 
between GB and North America, the probability of at least one person travelling 
to/from a CWD affected area and, in doing so, contaminating their clothing, 
footwear and/or equipment prior to arriving in GB is greater than negligible. 
For deer hunters, specifically, the risk is likely to be greater given the 
increased contact with deer and their environment. However, there is significant 
uncertainty associated with these estimates. 
snip... 
Therefore, it is considered that farmed and park deer may have a higher 
probability of exposure to CWD transferred to the environment than wild deer 
given the restricted habitat range and higher frequency of contact with tourists 
and returning GB residents. 
snip... 
CHRONIC WASTING DISEASE CWD TSE PRION, how much does it pay to find CWD $$$ 
CWD, spreading it around... 
for the game farm industry, and their constituents, to continue to believe 
that they are _NOT_, and or insinuate that they have _NEVER_ been part of the 
problem, will only continue to help spread cwd. the game farming industry, from 
the shooting pens, to the urine mills, the antler mills, the sperm mills, velvet 
mills, shooting pens, to large ranches, are not the only problem, but it is 
painfully obvious that they have been part of the problem for decades and 
decades, just spreading it around, as with transportation and or exportation and 
or importation of cervids from game farming industry, and have been proven to 
spread cwd. no one need to look any further than South Korea blunder ; 
=========================================== 
spreading cwd around... 
Between 1996 and 2002, chronic wasting disease was diagnosed in 39 herds of 
farmed elk in Saskatchewan in a single epidemic. All of these herds were 
depopulated as part of the Canadian Food Inspection Agency’s (CFIA) disease 
eradication program. Animals, primarily over 12 mo of age, were tested for the 
presence CWD prions following euthanasia. Twenty-one of the herds were linked 
through movements of live animals with latent CWD from a single infected source 
herd in Saskatchewan, 17 through movements of animals from 7 of the secondarily 
infected herds. 
***The source herd is believed to have become infected via importation of 
animals from a game farm in South Dakota where CWD was subsequently diagnosed 
(7,4). A wide range in herd prevalence of CWD at the time of herd depopulation 
of these herds was observed. Within-herd transmission was observed on some 
farms, while the disease remained confined to the introduced animals on other 
farms. 
spreading cwd around... 
Friday, May 13, 2011 
Chronic Wasting Disease (CWD) outbreaks and surveillance program in the 
Republic of Korea 
Hyun-Joo Sohn, Yoon-Hee Lee, Min-jeong Kim, Eun-Im Yun, Hyo-Jin Kim, 
Won-Yong Lee, Dong-Seob Tark, In- Soo Cho, Foreign Animal Disease Research 
Division, National Veterinary Research and Quarantine Service, Republic of Korea 
Chronic wasting disease (CWD) has been recognized as an important prion 
disease in native North America deer and Rocky mountain elks. The disease is a 
unique member of the transmissible spongiform encephalopathies (TSEs), which 
naturally affects only a few species. CWD had been limited to USA and Canada 
until 2000. 
On 28 December 2000, information from the Canadian government showed that a 
total of 95 elk had been exported from farms with CWD to Korea. These consisted 
of 23 elk in 1994 originating from the so-called “source farm” in Canada, and 72 
elk in 1997, which had been held in pre export quarantine at the “source 
farm”.Based on export information of CWD suspected elk from Canada to Korea, CWD 
surveillance program was initiated by the Ministry of Agriculture and Forestry 
(MAF) in 2001. 
All elks imported in 1997 were traced back, however elks imported in 1994 
were impossible to identify. CWD control measures included stamping out of all 
animals in the affected farm, and thorough cleaning and disinfection of the 
premises. In addition, nationwide clinical surveillance of Korean native 
cervids, and improved measures to ensure reporting of CWD suspect cases were 
implemented. 
Total of 9 elks were found to be affected. CWD was designated as a 
notifiable disease under the Act for Prevention of Livestock Epidemics in 2002. 
Additional CWD cases - 12 elks and 2 elks - were diagnosed in 2004 and 
2005. 
Since February of 2005, when slaughtered elks were found to be positive, 
all slaughtered cervid for human consumption at abattoirs were designated as 
target of the CWD surveillance program. Currently, CWD laboratory testing is 
only conducted by National Reference Laboratory on CWD, which is the Foreign 
Animal Disease Division (FADD) of National Veterinary Research and Quarantine 
Service (NVRQS). 
In July 2010, one out of 3 elks from Farm 1 which were slaughtered for the 
human consumption was confirmed as positive. Consequently, all cervid – 54 elks, 
41 Sika deer and 5 Albino deer – were culled and one elk was found to be 
positive. Epidemiological investigations were conducted by Veterinary 
Epidemiology Division (VED) of NVRQS in collaboration with provincial veterinary 
services. 
Epidemiologically related farms were found as 3 farms and all cervid at 
these farms were culled and subjected to CWD diagnosis. Three elks and 5 
crossbreeds (Red deer and Sika deer) were confirmed as positive at farm 2. 
All cervids at Farm 3 and Farm 4 – 15 elks and 47 elks – were culled and 
confirmed as negative. 
Further epidemiological investigations showed that these CWD outbreaks were 
linked to the importation of elks from Canada in 1994 based on circumstantial 
evidences. 
In December 2010, one elk was confirmed as positive at Farm 5. 
Consequently, all cervid – 3 elks, 11 Manchurian Sika deer and 20 Sika deer – 
were culled and one Manchurian Sika deer and seven Sika deer were found to be 
positive. This is the first report of CWD in these sub-species of deer. 
Epidemiological investigations found that the owner of the Farm 2 in CWD 
outbreaks in July 2010 had co-owned the Farm 5. 
In addition, it was newly revealed that one positive elk was introduced 
from Farm 6 of Jinju-si Gyeongsang Namdo. All cervid – 19 elks, 15 crossbreed 
(species unknown) and 64 Sika deer – of Farm 6 were culled, but all confirmed as 
negative. 
Friday, August 07, 2015 
Texas CWD Captive, and then there were 4 ? 
Thursday, August 06, 2015 
WE HAVE LOST TEXAS TO CWD TASK FORCE CATERING TO INDUSTRY 
HAVE YOU BEEN THUNDERSTRUCK ? 
Thursday, July 24, 2014 
*** Protocol for further laboratory investigations into the distribution of 
infectivity of Atypical BSE SCIENTIFIC REPORT OF EFSA New protocol for Atypical 
BSE investigations 
Friday, August 14, 2015 
*** Susceptibility of cattle to the agent of chronic wasting disease from 
elk after intracranial inoculation ***
Wednesday, July 15, 2015 
*** Additional BSE TSE prion testing detects pathologic lesion in unusual 
brain location and PrPsc by PMCA only, how many cases have we missed? 
Wednesday, July 29, 2015 
Further characterisation of transmissible spongiform encephalopathy 
phenotypes after inoculation of cattle with two temporally separated sources of 
sheep scrapie from Great Britain 
Wednesday, July 29, 2015 
Porcine Prion Protein Amyloid or mad pig disease PSE 
Monday, August 10, 2015 
Detection and Quantification of beta-Amyloid, Pyroglutamyl A beta, and Tau 
in Aged Canines 
http://caninespongiformencephalopathy.blogspot.com/2015/08/detection-and-quantification-of-beta.html
Friday, August 7, 2015 
Transgenic Mouse Bioassay: Evidence That Rabbits Are Susceptible to a 
Variety of Prion Isolates 
Thursday, August 13, 2015 
Iatrogenic CJD due to pituitary-derived growth hormone with genetically 
determined incubation times of up to 40 years
Thursday, January 15, 2015 
41-year-old Navy Commander with sporadic Creutzfeldt–Jakob disease CJD TSE 
Prion: Case Report 
Subject: *** Becky Lockhart 46, Utah’s first female House speaker, dies 
diagnosed with the extremely rare Creutzfeldt-Jakob disease aka mad cow type 
disease 
what is CJD ? just ask USDA inc., and the OIE, they are still feeding the 
public and the media industry fed junk science that is 30 years old. 
why doesn’t some of you try reading the facts, instead of rubber stamping 
everything the USDA inc says. 
sporadic CJD has now been linked to BSE aka mad cow disease, Scrapie, and 
there is much concern now for CWD and risk factor for humans. 
My sincere condolences to the family and friends of the House Speaker Becky 
Lockhart. I am deeply saddened hear this. 
with that said, with great respect, I must ask each and every one of you 
Politicians that are so deeply saddened to hear of this needless death of the 
Honorable House Speaker Becky Lockhart, really, cry me a friggen river. I am 
seriously going to ask you all this...I have been diplomatic for about 17 years 
and it has got no where. people are still dying. so, are you all stupid or 
what??? how many more need to die ??? how much is global trade of beef and other 
meat products that are not tested for the TSE prion disease, how much and how 
many bodies is this market worth? 
Saturday, January 17, 2015 
*** Becky Lockhart 46, Utah’s first female House speaker, dies diagnosed 
with the extremely rare Creutzfeldt-Jakob disease 
*** ALERT new variant Creutzfeldt Jakob Disease nvCJD or vCJD, sporadic CJD 
strains, TSE prion aka Mad Cow Disease United States of America Update December 
14, 2014 Report *** 
Terry S. Singeltary Sr. 

 
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