Incubation of ovine scrapie with environmental matrix results in biological and biochemical changes of PrPSc over time
Veterinary Researchvolume 46, Article number: 46 (2015)
Ovine scrapie can be transmitted via environmental reservoirs. A pool of ovine scrapie isolates were incubated on soil for one day or thirteen months and eluted prion was used to challenge tg338 mice transgenic for ovine PrP. After one-day incubation on soil, two PrPSc phenotypes were present: G338 or Apl338ii. Thirteen months later some divergent PrPSc phenotypes were seen: a mixture of Apl338ii with either G338 or P338, and a completely novel PrPSc deposition, designated Cag338. The data show that prolonged ageing of scrapie prions within an environmental matrix may result in changes in the dominant PrPSc biological/biochemical properties.
Introduction, methods and results
Prion diseases (or transmissible spongiform encephalopathies, TSEs) are fatal, progressive neurological disorders that have no effective treatment or cure. Prion diseases include human Creutzfeldt-Jakob disease (CJD), bovine spongiform encephalopathy (BSE), scrapie in sheep and goats, and chronic wasting disease (CWD) in deer and elk. The prion hypothesis states that the causal agent is a misfolded version of the cellular prion protein (PrPC), termed PrPSc .
It is known that particular prion diseases can include strains that display distinct and reproducible disease phenotypes. It is most likely that the prion agent is not a single entity but is made up of a plethora of different conformers of PrPSc and the dominant PrPSc conformation causes the specific disease characteristics for a particular infection including pathology, clinical signs and PrPSc molecular signatures . The identification of prion strains is in fact therefore a description of the dominant disease characteristics. The “gold standard” method employed to define scrapie strains is mouse bioassay using either wild type or preferably transgenic mice such as the tg338 line . These transgenic mice overexpress an ovine PrP transgene and display high sensitivity and specificity to ovine scrapie prions. Of the several phenotypic parameters exhibited in a host species which are used to discriminate TSEs, PrPSc distribution in the brain detected by immunohistochemistry (IHC) or PET/Histo-blot offers the highest discriminatory power and it can be applied on an individual mouse basis [4-8]. This biological property of prions in conjunction with analysis of the biochemical properties of the agent recovered from the same host species offer a powerful means to identify TSE strains even when they are applied at primary passage as they remain essentially unchanged through serial passages [4,6,9,10].
Scrapie is effectively transmitted between susceptible sheep and goats by animal-to-animal contact and via environmental reservoirs, a disease trait that is shared with CWD in deer/elk. For both diseases, the agent is disseminated widely in vivo and excreted/secreted via multiple routes (reviewed in ). The likely location of environmental reservoirs are water, soil, metal surfaces, wood surfaces and concrete surfaces ([12,13] reviewed in ). Furthermore, environmental prion is stable and remains infectious for years .
The purpose of the present study was to assess the viability of scrapie prions in a soil matrix over time. Pools of hindbrain from nine scrapie-infected sheep with VRQ/VRQ (amino acid positions 136, 156 and 171 respectively) PRNP genotypes and twenty genotype matched scrapie-free controls were made into homogenates and applied to soil columns containing a sandy loam soil as previously described . Soil columns were kept at 16–20 °C and constant water content and sampled 1 day and 13 months after the addition of the prion sample. Equivalent samples were taken for soil incubated with the prion-free control sample, and soil unexposed to brain material was used as a further control. All soil was removed from a column and homogenised by mixing. Prion protein was then extracted from soil : 100 mg of soil was re-suspended for 1 h in 500 μL PBS prior to centrifugation at 800 g for 10 min. The soil pellet was re-suspended in 100 μL of 1% (w/v) SDS in PBS and shaken vigorously for 1 h. After centrifugation at 800 g for 10 min prion protein in the supernatant was removed. Extracted prion was then precipitated for 30 min at 37 °C by the addition of 15 μL of 4% (w/v) sodium phosphotungstic acid (Napta) and 170 mM magnesium chloride, and recovered by centrifugation at 12 100 g for 30 min. The pellet was air-dried and re-suspended in 20 μL sterile saline. Each inoculum (20 μL) was used to challenge intracranially 5–10 week old tg338 mice (n = 10) as described previously . After inoculation the mice were monitored for signs of neurological disease and were euthanized after exhibiting clinical signs. All animal work was approved by the Animal and Plant Health Agency local ethics committee and was carried out in accordance with the Animals (Scientific Procedures) Act 1986 under Home Office project license 70/6310. In combination with clinical signs, immunohistochemical (IHC) analysis was used to diagnose prion infection for all mice in the study. After euthanasia the brain of each mouse was removed and processed as described previously . TSE diagnosis was based on PrPSc detection in brain sections with polyclonal antibody Rb486 following a standard protocol . Identification of different PrPSc types and their distribution in the murine brain was used to identify defined PrPSc distribution patterns as described previously for wild type and transgenic mice [4-7]. Slides were analysed blind by two independent observers (J.S. and C.V.); the agreement between the two observers regarding PrPSc deposition pattern identification was 100%.
With inoculum extracted from soil incubated with the scrapie sample for 1 day, eight out of the 10 challenged mice succumbed to TSE with incubation periods <170 days post inoculation (dpi) (Figure 1A). IHC analysis of the mice revealed granular PrPSc deposits distributed mainly along the brainstem, thalamus and basal ganglia with little involvement of the cerebral or cerebellar cortex; this pattern has been previously designated as G338 (Figure 2A) . One further mouse died 483 dpi (Figure 1A) and the main PrPSc pattern feature was plaques and large aggregates of PrPSc in the brain parenchyma and perivascular plaques in round meningeal vessels (Figure 2B), a distribution pattern previously recorded as Apl338ii. One mouse that died 243 dpi was TSE negative and was treated as an intercurrent death. No mice displayed signs of TSE between 170–483 dpi.
After 13 months incubation of the scrapie sample on soil, prions were extracted and inoculated into tg338 mice. One mouse was diagnosed TSE negative (intercurrent death) and the remaining nine were TSE positive. The incubation period of the TSE positive mice was 606–748 dpi (Figure 1A). With one exception all mice showed a pattern that was compatible with Apl338ii. This was the only pattern observed in four mice, while in another three it was observed in conjunction with G338 (Figures 2D-F) and in a single mouse signs of Apl338ii and P338 were observed concomitantly (Figure 2G). P338 is a pattern characterised by punctate deposits in the neuropil and prominent well-defined intraneuronal PrPSc accumulations as described previously . One mouse also showed a previously unrecognised PrPSc pattern designated Cag338 characterised by granular PrPSc deposits, which increased in intensity multifocally, to give rise to coalescing aggregates in the neuropil (Figure 2C). The areas affected more extensively were the midbrain and the medulla.
Previous studies have shown that the P338 IHC presentation of PrPSc is accompanied by a relatively low molecular weight for the PK-resistant PrPSc compared to both Apl338ii and G338 [4,6]. We looked to investigate whether the distinct IHC presentations described here were accompanied by distinct PrPSc properties. Both the original sheep samples and the murine samples were digested with PK, analyzed on western blots and the prion detected with the antibody SHa31 as previously described  (Figures 3A and B). The results show that all ovine samples had indistinguishable PrPSc profiles with an unglycosylated PrPSc size of 19.0 +/− 0.3 kDa. The G338, Apl338ii and G338/Apl338ii mixed IHC phenotypes had a similar size of 19.1 +/− 0.3 kDa. However, the Apl338ii/P338 mixed phenotype had a relatively low molecular mass by comparison of 17.1 kDa, consistent with previously published data for P338 [4,6]. Also, the unglycosylated PrPSc of Cag338 had a relatively high molecular mass of 20.6 kDa (Figure 3B). In addition, we determined that the G338 and Apl338ii IHC phenotypes could be readily distinguished by the stability of their PrPSc (Figures 3C and D). The assay was carried out as described previously . Briefly, aliquots of each murine brain homogenate were incubated with increasing molar concentrations of GdnHCl (final concentrations of 0.5, 2.5, 3.0, 3.5, and 4 M) 1 h at 37 °C. Subsequently all samples were adjusted to a final GdnHCl concentration of 0.4 M, proteinase K was added to a final concentration of 50 μg/mL and the samples incubated for 1 h at 37 °C. Reactions were stopped with 5 mM PMSF. Samples were analysed by western blot using antibody SHa31. The level of signal for each PrP triplet treated with 2.5, 3.0, 3.5 or 4 M GdnHCl was expressed as a percentage of the signal for the same sample treated with 0.5 M. G338 was more susceptible to GdnHCl treatment becoming PK sensitive after treatment with 3 M of the denaturant. In contrast, Apl338ii was relatively stable to denaturation with readily detectable PK-resistant PrPSc after treatment with 4 M GdnHCl (Figures 3C and D). Overall, the PrPSc biochemical characteristics were distinct for each of Apl338ii, G338, Apl338ii/P338 mixed and Cag338 IHC phenotypes.
Extracts from soil unexposed to brain material and soil treated with scrapie-free brain homogenate were bioassayed in tg338 mice and were TSE negative.
For comparison, the original scrapie sample without any incubation with soil was also titrated in tg338 mice over a range of 10-fold dilutions (n = 10 mice for each dilution; Figure 1B). All mice challenged with 20 μg and 2 μg scrapie brain succumbed to scrapie with a G338 IHC phenotype. Only one of the 10 mice challenged with either 200 or 20 ng of brain pool was diagnosed with scrapie and in each case this produced an Apl338ii IHC phenotype. Challenge with lower amounts of brain pool did not cause disease. Prion desorbed from soil after 1 day displayed the same IHC and PrPSc phenotypes as the original scrapie pool, that is Apl338ii and G338. However, it is possible that the extraction and precipitation treatments have an effect on PrPSc phenotype or recovery. To test this, murine brain homogenates for G338 and Apl338ii phenotypes (10% w/v; 100 μL) were diluted to 200 μL with 2% (w/v) SDS and shaken vigorously for 1 h. After centrifugation at 800 g for 10 min prion in the supernatant was precipitated with Napta and brain homogenate and Napta precipitate were analyzed by western blot as detailed above and the total signal for the PrP triplet was determined by densitometry. The percentage recovery after SDS treatment/Napta precipitation for each isolate was determined and comparison of the recoveries of G338 and Apl338ii was carried out using a two-tailed students t-test. The percentage recoveries for 3 isolates of murine G338 and 2 isolates of murine Apl338ii were determined and the mean recoveries were 57 and 56% respectively, differences in the recoveries of the two PrPSc phenotypes were not significant (p = 0.97). In addition, the molecular phenotypes were maintained before and after SDS/Napta treatment (Figures 3C and D).
The bioassay data show that the hit rate was equivalent for sheep scrapie extracted from soil after 1 day or 13 months incubation indicating ovine scrapie infection was retained on soil over a prolonged time period. The data also clearly suggest that between day 1 and month 13 the biological and biochemical properties of the prion that is desorbed from soil change considerably. In our view, this concomitant change of biological and biochemical properties as described here is indicative of strain variation. Indeed many of these phenotypic characteristics have been attributed to characterised strains isolated and studied in tg338 mice (Table 1) [4,6]. Some of the strain phenotypes identified after a 13 month incubation are highly novel. Both G338 and P338 strains are relatively fast incubation strains and have not been reported before in a mixed phenotype with Apl338ii or at these prolonged incubation times. The identification particularly of G338 IHC characteristics, in conjunction with Apl338ii, in the brains of mice showing incubation period >600 dpi is intriguing as the maximum incubation period associated with G338 is known to be <200 dpi . Therefore the possibility that G338 was existing as an independent entity in the inoculum used to challenge the mice is unlikely even if we accept that in the presence of a significantly slower strain, such as Apl338ii, the propagation of G338 was delayed. Another possible explanation would be that agents with G338 or P338 properties could emerge from Apl338ii at a later stage of the incubation period. Alternatively the G338 and P338 phenotypic characteristics that were observed in conjunction with Apl338ii indicate phenotypes that have some G338 or P338 properties associated with unusually prolonged incubation periods. Without isolating each of these agents in a pure state to study their properties it is not possible to draw definitive conclusions regarding their exact strain characteristics. However, their existence at this stage, particularly of the P338 IHC phenotype, which is also accompanied with biochemical properties that are attributed to the P338 strain, cannot be ignored and adds valuable information regarding the diversity of scrapie phenotypes that can emerge after prolonged incubation period with soil. The Cag338 strain phenotype is reported here for the first time. Collectively, therefore, these data suggest that the ageing of prions within an environmental matrix can affect their biological and biochemical properties suggesting strain alterations. The three novel phenotypes of desorbed prion strains observed after 13 months incubation on soil were not detected in a range of 10-fold dilutions of the original scrapie sample and the SDS/Napta treatment of samples to desorb them from soil had no apparent effect on G338 or Apl338ii recovery or PrPSc phenotype. Therefore, these novel PrPSc presentations must be a consequence of their interaction with soil or ageing or both. It is not known whether this emergence of novel phenotypes seen here during ageing on soil reflects the selection of existing conformers present in the original sample or de novo mutation to produce novel conformations of the prion. The study compared PrPSc phenotypes that are recovered from soil after 1 day and 13 month periods and the effects of soil interaction and incubation time alone are not considered separately. Therefore it is also not known whether the observed changes in dominant prion strains are dictated by incubation time at ambient temperature alone or by interaction with soil over a prolonged period. However, regardless of the mechanisms of the observed ageing, the unequivocal finding is that when a mixture of prion phenotypes are added to a soil environment the dominant pathologies change over time. Whether analogous ageing of prions occurs in other natural environments that may harbour prion reservoirs remains to be established. The presence of “dynamic” reservoirs of environmental scrapie infectivity could possibly lead to the emergence of novel strains of scrapie in natural infections. Such events may have contributed to the significant (and unusual) diversity of the scrapie disease agent.
Transmissible spongiform encephalopathy
Chronic wasting disease
- PrP/PrPC :
Cellular prion protein
- PrPSc :
Disease-associated prion protein
Sodium phosphotungstic acid
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This work was supported by the Department for Environment, Food and Rural Affairs, UK (Defra project SE1858). The authors would like to thank colleagues in Pathology and Animal Science Unit at APHA for their skilled technical expertise and support. We thank the Biological-archive, APHA (Addlestone, Surrey, UK) for the provision of sheep brain material.
The authors declare that they have no competing interests.
KCG and BCM conceived this study and participated in its design and coordination. JS, RL and CMV carried out the bioassay JS and CMV conducted IHC analysis of the samples and the interpretation of the findings. JO, KB and CB carried out the soil experiments and prepared the inoculums, analysed samples by western blot and conformational stability assay. KCG and BCM have written the manuscript with inputs from all authors. All authors read and approved the final manuscript.