The Ecology of Prions

THE EMERGENCE OF CWD

The discovery of CWD happened incrementally, and over this time, CWD became endemic in both free-ranging and captive animal herds. A population of captive deer being held in wildlife facilities in Colorado from 1967 to 1979 were noted to have been experiencing the same group of clinical signs, including weight loss, torpor, polydipsia, polyuria, low urine specific gravity, and hypotonia. Histopathological changes were noted in brain tissue and included spongiform degeneration and vacuolization (3). There were similarities to other TSEs, both human and animal, but no evidence of CWD transmission, only some indirect contact between animals at fence lines. Two years later, the same researchers reported disease phenotypes in Rocky Mountain elk and in free-ranging cervids as well (16). Amyloid plaques were also noted in the brains of affected deer (17). Intracranial inoculation of brain homogenates from affected deer into naive deer and ferrets transmitted CWD after an incubation time of 17 to 24 months (4, 18). Prion amyloids found in the brains of CWD-affected elk and deer provided evidence of CWD sharing the same etiology and pathology as those of other TSEs (19, 20).

The origin of CWD is still widely contested. It remains uncertain whether CWD arose spontaneously as a sporadic incident in one or a few free-ranging or captive deer and then spread to other cervids across landscapes. No evidence demonstrates CWD being caused by infected feed or feed products, as occurred in cattle to cause bovine spongiform encephalopathy (BSE) (21, 22). The scrapie-BSE nexus drives one popular hypothesis that scrapie crossed the species barrier from sheep to deer when animals were housed concurrently in Colorado facilities. It may then have spread to and from free-ranging animals when they came into fence-line contact with captive animals (4). Most, if not all, CWD cases can be tracked back to movement of infected captive cervids from the initial epicenter in northern Colorado and southern Wyoming to game farms throughout North America and South Korea, supporting that hypothesis. While not linked to CWD emergence in North America, new CWD cases recently discovered in Norway (15) may be attributed to free-ranging reindeer and moose acquiring the disease from sympatric scrapie-infected sheep. However, the relatively facile spontaneous conversion of cervid PrP^C to CWD prions in vitro (23) suggests that CWD may occur spontaneously, like scrapie or sporadic Creutzfeldt-Jakob disease (CJD).

Numerous PRNP gene polymorphisms increase susceptibility or resistance to disease in deer and elk. The most common mule deer genotypes at codons 95, 96, 132, 138, and 225 encode glutamine (Q), glycine (G), serine (S), methionine (M), and serine (S), respectively. Less common polymorphisms include histidine (H) at codon 95, S96, leucine (L) at codon 132, asparagine (N) at codon 138, and phenylalanine (F) at codon 225. Transgenic mouse experiments convincingly show that the more common genotypes correlate with increased susceptibility to CWD (24–26). Comparisons between free-ranging and captive Rocky Mountain elk linked CWD susceptibility to M132 homozygosity (25). Most genotyped CWD-negative deer from Wisconsin expressed genotypes linked to CWD-positive deer, revealing a huge deer population susceptible to CWD (24). Evidence that resistant genotypes provide delayed onset or prolonged incubation periods has been shown, but these genotypes are rarely found in large populations (27–29). These data alert surveillance and other wildlife management agencies to be aware of the susceptible populations in their areas and to possibly mitigate continued spread based on this information.

ROLE FOR THE ENVIRONMENT IN INDIRECT CWD TRANSMISSION

In the 1940s, shepherds in northern Iceland culled their entire sheep population in an effort to eradicate Maedi, an ovine lung disease rampant in their flocks. The area in which the culling took place overlapped areas where evidence supported the presence of scrapie, the prion disease of sheep. Healthy sheep from an area with no evidence of scrapie were introduced into this area. After 3 years, the new animals became sick with scrapie (30–32). In 1978, Iceland again tried to eradicate scrapie by imposing strict implementations, including culling positive and at-risk animals, disinfecting or destroying buildings that housed infected animals, banning translocation of animals and equipment from positive farms, restocking farms after at least two dormant years, and continued surveillance. After 16 years, some of the reintroduced flocks developed clinical scrapie (30). Because these flocks had been scrapie-free through several generations, the environmental persistence of scrapie prions on these farms likely contributed to the emergence of new scrapie cases in these sheep.

Similar environmental persistence has been noted with CWD. The Foothills Wildlife Research Facility (FWRF) in Fort Collins, CO, where CWD was originally detected, underwent a similar cleansing and culling in order to eradicate CWD and to establish new, CWD-free herds. Approximately 2 years after reintroduction of elk herds to the FWRF, animals began showing clinical signs of illness. These decontamination failures implicated environmental reservoirs in the reemergence of CWD in these herds, all of whose members were acquired from Rocky Mountain National Park as calves, born to wild free-ranging dams, when they were less than 1 week old (33). While the reoccurrence of infection may have been from environmental persistence and indirect transmission of cervid prions, vertical transmission from positive mothers infecting their calves also may have occurred. As CWD progressed, animals may have begun shedding prions, leading to both a direct contact source between elk and an indirect source via accumulation in paddocks. An experimental demonstration of indirect environmental reservoir transmission was shown in 2004, when uninfected mule deer were housed in paddocks containing either infected deer or a positive deer carcass decomposed 20 months prior or in an empty paddock containing excreta from positive deer housed 26 months prior. Uninfected deer became CWD positive in all three scenarios (34). CWD transmission increases during winter, possibly due to density-dependent transmission. Deer herds stay together over winter, which may increase the chance of both direct transmission and contacting accumulated positive environmental material. Indeed, the prevalence of CWD has been shown to be much higher in defined winter ranges, which may be due to an accumulation of PrP-positive material in these areas (35).

Bedding and water transferred from indoor rooms housing CWD-positive deer transmitted CWD to negative deer in prion-naive rooms in only 15 months. Tonsil biopsy confirmed the presence of PrP^CWD in one of two animals (13). Both animals eventually contracted CWD solely through environmental exposure. Given the overwhelming evidence that prions resist degradation, persist in the environment for years (30), and can be shed in excreta of clinical as well as asymptomatic animals (12, 36–39), CWD prions likely accumulate in the environment. Estimation of prion titers by mouse bioassay of CWD prions intracerebrally inoculated into susceptible animals indicates that a single experimentally inoculated deer can defecate 10.9 log 50% lethal dose (LD₅₀) units of CWD prions over a 10-month period, a typical duration of CWD (39). The same deer can also urinate up to 6 log LD₅₀ units of prions into the environment over this time. Naturally infected deer defecate an estimated 1,000 LD₅₀ units of CWD prions daily (12). While these doses are relatively low, repeated frequent exposure, either direct or indirect, increases the likelihood of contracting CWD (7, 40).

POTENTIAL ENVIRONMENTAL PRION RESERVOIRS AND VECTORS

Researchers are currently investigating at least three potential environmental reservoirs for prions—soil, water, and plants. These proposed reservoirs most likely accumulate prions deposited from excreta and decaying carcasses. Other fomites in the environment, such as salt licks, wallows, fences, bedding sites, and even buildings, may also contribute to prion deposition in the environment (13, 30, 41, 42).

Deer and elk ingest small but appreciable amounts of soil (<2% soil consumption in the diet) (7, 43). They often ingest soil inadvertently while feeding, but they may also intentionally eat soil to obtain micronutrients essential to their metabolism. These considerations led researchers to begin looking for prions in soil and to determine whether PrP^C binds soil and/or its constituents and if the prion infectivity and/or conformation changes in a soil environment. One study looked at the potential ability of PrP^C to misfold into the pathological prion structure when bound to a mineral-phase soil component known as montmorillonite (MTE) (44). While PrP-MTE complexes were formed and some α-helical-to-β-sheet-like structural changes occurred, these structural transformations were distinct from the pH-induced conformational changes that occur during prion formation and did not produce infectious prions. Similar work demonstrated that prions could also adsorb to MTE, microparticles of quartz, kaolinite (another mineral-phase soil component), and a variety of whole soils (45). MTE bound prions so tightly that 10% sodium dodecyl sulfate was required for desorption and resulted in N-terminal truncation of PrP^RES. Prions present in a complex matrix of infected brain homogenate adsorbed to MTE much more slowly, which likely mimics environmental contamination (46). Experimental evidence shows that unbound prions degrade over time, while soil-bound prions remain at stable or increasing levels (47, 48), suggesting that prions remain stable in the environment when bound to soil or clay components and potentially become more infectious. Prions remained infectious when bound to MTE and inoculated intracranially into rodents (49). MTE was recently shown to increase the environmental stability and bioavailability of prions bound to it (7). However, when prions were subjected to simulated weather conditions, such as heating, wetting, and drying, MTE actually potentiated prion degradation (50). Microbial communities in soil, compost, and lichens also demonstrate significant reductions of prion titers (51–53). Thus, natural and cultivated microbial communities may mitigate some, but not all, environmental prion contamination.

Prions that do survive environmental insult maintain or even augment prion transmission. Prion infectivity and oral transmission increased when PrP was bound to soil (54). Intranasal inoculations of deer with prions bound to MTE dust particles resulted in efficient transmission of CWD (55). Soil-bound prions resist rumen digestion, and MTE enhances the bioavailability and retention of prions bound to it (56). This high affinity of MTE for prions potentially may be exploited as a therapeutic or decontaminant to remove PrP from complex solutions.

Nichols et al. found PrP^RES in water collected from an area in Colorado where CWD is endemic and from raw water samples collected in a nearby water treatment facility (11). BSE prions survived in raw sewage, with little or no reduction in infectivity (57), and organic matter present in water partially prevented degradation of PrP^RES and loss of infectivity (58, 59). Fomites from infected deer, including water, transmitted CWD prions to uninfected deer with no direct contact with infected cohorts (13).

Detection of prions in soil, water, excreta, and decaying carcasses on the landscape raises legitimate concern about whether plants, the main food source of deer and elk, can act as prion vectors by active uptake or passive contamination. Plants take up protein, as a nitrogen source, and other nutrients in their roots, stems, and aerial tissues (60–62). Endophytic bacteria and bacterial communities that fix nitrogen and fight plant diseases have been described (61, 63, 64). Plants may conceivably take up prions from soil or water into their root systems or aerial tissues or become surface contaminated through saliva, urine, feces, and/or decaying CWD-infected carcasses. An attempt was made to assess the potential of wheat grass grown in agar medium to take up prions from water (65). Both roots and lower stems were examined for PrP^RES by using commercially available enzyme-linked immunosorbent assays for PrP^RES and an ultrasensitive prion detection assay, i.e., protein misfolding cyclic amplification (PMCA). The researchers reported finding PrP^RES inside roots but not stems, in addition to PrP^RES on stem and root surfaces that was rinsed away with water. PMCA experiments were inconclusive due to nonspecific amplification in control unexposed plant homogenates. Prion uptake was assessed for only one 24-h time point, and significant contamination issues were reported. Another group successfully used PMCA to detect prions taken into roots, stems, and leaves by wheat grass plants (Triticum aestivum L.) grown with high concentrations of prions spiked into soil (14). Since copious data show that soil binds prions extremely tightly, the mechanism by which prions move from soil to plants remains unclear. Perhaps the experimental conditions used soil saturated with prions and facilitated plant uptake of free prions. If so, these results may not be ecologically relevant, since one expects very low levels of prion contamination, except perhaps in areas just under a decaying infected carcass. More relevant experimental contamination of plants by spraying of infected brain homogenate onto wheat (Triticum aestivum L.) leaves resulted in detection of PrP^RES at a stable level for 49 days. Different plant tissues were also exposed to urine and feces from both CWD-positive animals and scrapie-infected hamsters, and the results again showed prions bound to the plant tissues after rinsing and drying.

Decaying carcasses of any kind affect the ecosystem around them, often leading to higher concentrations of nitrogen and a difference in plant species in the area that may be present for years after the initial decomposition. As a carcass decays, the body fluids released destroy the plants underneath and in the surrounding area, creating a zone of disturbance which, after time, becomes zones of fertility due to nutrients and limited competition from other species (66). Since CWD prions have been shown to persist in the environment, it is postulated that a decaying CWD-positive carcass can saturate the environment with prions, which can then be taken up into plants as growth of new flora occurs. Prions were detected in roots, stems, and leaves of wheat plants (Hordeum vulgar) grown in soil experimentally contaminated with prions (14). Cervids readily eat both wheat and barley grasses in the spring: around 4 to 64% of the mule deer diet is composed of grasses, while the remainder comes from shrubs and trees (67).

Reservoir or vector animals transmit many emerging infectious diseases that affect wildlife populations. No reservoir animals have been found for CWD, although several vector animals, including predators and scavengers, may aid in dissemination of CWD prions across the landscape. Coyotes (68), cougars (69), and even crows (70) have been investigated as potential CWD reservoirs and/or vectors. Experimentally inoculated coyotes and crows both shed infectious prions in their feces. Both mammalian and avian scavengers travel scores of kilometers per day and likely contribute to prion dissemination across their habitats and prion accumulation across landscapes. While cougars prey more successfully on CWD-affected cervids than on unaffected cervids, no evidence exists that cougars have contracted feline spongiform encephalopathy as a result. Thus, if they contribute to prion dissemination, they likely do so as vectors, not reservoirs.

Even if reservoir species do exist, they likely replicate prions as a new strain that likely exhibits altered host ranges and introduces new species barriers to cervids and other mammals that contact them. But Bian et al. recently demonstrated nonadapted prion amplification (NAPA) experimentally in vitro and in vivo (71), so host range restriction by reservoir animals may not be absolute. If NAPA occurs in nature, prion dissemination may aid environmental prion reservoirs to perpetuate CWD via indirect transmission. In the absence of CWD reservoir animals, translocation of CWD-infected cervids often facilitates emergence, because it can bring susceptible naive animals in contact with infected ones and their contaminated environments (72), providing proximity to CWD prion reservoirs for both direct and indirect transmission.

MODELING INDIRECT PRION TRANSMISSION DYNAMICS

Mathematical models of CWD prevalence and dynamics support the hypothesis that direct transmission certainly accounts for most transmission events, with both population density and contact frequency contributing to CWD spread (9, 73). However, modeling of only direct transmission failed to account for data showing high and increasing prevalences in areas of endemicity (74, 75). Modeling of exposure risks of sheep flocks to scrapie identified buildings and pastures as likely sources of indirect scrapie transmission (76). Models of CWD transmission that include both direct and indirect parameters more closely match the available data on current epidemics seen in Colorado, Wyoming, and Wisconsin (6, 10). Miller et al. compared seven different CWD transmission models and found that those including indirect transmission parameters matched existing data four times more accurately than those modeling only direct transmission (75). Including landscape effects derived from GPS data in areas of Alberta, Canada, where CWD is endemic increased the precision of models using density parameters (8). Bayesian models assuming a long prion half-life implicate a significant role for indirect CWD prion exposure in CWD transmission dynamics due to accumulating prions in the environment (74, 77). They also model a slowly progressing disease that predicts a potential nonfatal carrier state that may ameliorate population decline initially but accelerate transmission as environmental contamination mounts, a conclusion corroborated by another model considering prolonged environmental prion persistence (78). Repeated sampling of the same mule deer populations in Colorado informed another Bayesian hierarchical model that predicted a steady population decline that could be slowed by hunter harvest, vehicular deaths, and predation (6). Few data or models predict sex-dependent transmission, although one model predicted that sex-specific differences fit frequency-dependent transmission models better (9). However, the authors included no indirect transmission parameter in their model, which may not accurately fit existing data dependent on the level of environmental accumulation. CWD prevalence continues to increase from Wyoming to Wisconsin to Arkansas, with these areas of endemicity reporting estimates ranging from 15 to 50% for free-ranging populations (47). With CWD spreading unabated, prion loads accumulating and persisting on landscapes, and the prevalence continuing to increase, both mathematical models and epidemiological data suggest that a tipping point may be reached, potentially resulting in herd decimation and population decline, especially in the presence of environmental reservoirs that retain prions for extended periods.

MITIGATING ENVIRONMENTAL PRION CONTAMINATION

Continued spread of CWD is clearly a multifaceted event. Prion persistence, indirect transmission, genetics, population density, contact frequency, management strategies, and other unrealized factors all may affect CWD ecology. Emerging data support a possibly significant role of soil, water, feces, and plants as prion reservoirs contributing to environmental contamination and indirect CWD transmission. CWD has now been found in cervids in 22 U.S. states, 2 Canadian provinces, South Korea, and Norway (5, 15). As CWD continues to unabatedly establish endemicity wherever it appears, eliminating or reducing environmental prion loads across landscapes represents a critical but enormous challenge.

Researchers have demonstrated that composting, incineration, and enzyme treatments may help to degrade environmental PrP^RES (53, 79, 80). These studies have focused mainly on specified risk material (SRM) generated from abattoirs and commercial meat processing plants. Brown et al. detected residual prion infectivity even after incineration at 600°C, although the initial prion titer was over 10⁹ LD₅₀ units/g of tissue (80), which is well beyond realistic environmental prion titers. Composting reduces prion titers in SRM by a much more modest 1 to 2 log, with cultivation of a proteolytic microbiome eliminating another order of magnitude of infectivity (53). Robust prion oxidation by ozone treatment also reduces prion infectivity in SRM and contaminated wastewater, by several orders of magnitude (81, 82). These procedures may be effective for reducing the likelihood of contaminating environments proximal to industrial farming enterprises but are impractical or simply cannot be applied to massive areas contaminated by CWD prions deposited by infected cervids across three continents. Although sources of CWD prions that contaminate endemic environments contain low levels of prions, continuous prion deposition and sustained prion persistence in environmental reservoirs pose significant challenges for bioremediation. Infected free-ranging animals continuously shedding prions in the environment and large host ranges complicate environmental decontamination strategies, especially if free-ranging infected animals cannot be removed, cordoned, or quarantined and contaminated landscapes protected from infected cervids returning to those habitats. Recontamination will likely occur and population decline will likely result if mitigation strategies fail. More sampling and surveillance need to be undertaken to understand the extent of environmental contamination in different areas of endemicity, and new mitigation strategies should be explored.

Controlled burning of landscapes in North America helps to mitigate fire danger in drought-stricken areas, in some of which CWD is endemic. Burning of plants, feces, and topsoil in these areas may reduce the low-level prion infectivity present in these areas. While the burn temperature and duration are certainly much lower than those attained in the experiments for which Brown et al. reported residual prion infectivity, naturally CWD-contaminated areas certainly contain many orders of magnitude less prion infectivity than prion-infected SRM. Prescribed burning may sufficiently lower prion titers on landscapes to at least impede the indirect transmission of CWD. Combined with directed hunter harvests, systematic culling, and targeted implementation of CWD vaccines (83, 84), we may be able to stem the slow but steady spread of CWD across the landscape.

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