Volume 24, Number 6—June 2018
Novel Focus of Sin Nombre Virus in Peromyscus eremicus Mice, Death Valley National Park, California, USA
The deer mouse (Peromyscus maniculatus) is the primary reservoir for Sin Nombre virus (SNV) in the western United States. Rodent surveillance for hantavirus in Death Valley National Park, California, USA, revealed cactus mice (P. eremicus) as a possible focal reservoir for SNV in this location. We identified SNV antibodies in 40% of cactus mice sampled.
Hantaviruses constitute a worldwide group of predominantly rodentborne zoonotic pathogens, some of which have emerged as distinctive human health hazards. In North America, Sin Nombre virus (SNV) is the most widespread hantavirus and is of primary public health importance because of the high case-fatality rate (>35%) associated with hantavirus pulmonary syndrome (HPS) (1). The principal reservoir of SNV is the deer mouse, Peromyscus maniculatus (2), a habitat generalist. Evidence of virus infection can be detected in populations of these mice throughout their range (3). Several other hantavirus strains have been identified in other species of mice in the family Cricetidae, but pathogenicity of these strains to humans remains unresolved (4,5).
Field and laboratory studies in North America have confirmed a close association between rodent species and specific hantavirus strains; limited sustained interspecies infection have been documented (6). In California, detection of elevated serum antibody titers to hantavirus in rodents other than deer mice have been assumed to represent El Moro Canyon virus in western harvest mice (Reithrodontomys megalotis); Isla Vista virus in California voles (Microtus californicus); Limestone Canyon virus in brush mice (P. boylii); or “spillover” of SNV infection from P. maniculatus to other species (1). It is not uncommon to detect serum antibodies to SNV in a small percentage (<5%) of sampled species that share habitat with P. maniculatus mice, including the closely related P. boylii, P. fraterculus, P. eremicus, and P. truei mice, as well as wood rats, Neotoma spp. (3). In California, SNV-seropositive rodents typically have not been found to exceed the average P. maniculatus infection prevalence of ≈14%, although infection prevalence estimates have slightly exceeded 14% among certain populations of R. megalotis mice (3,7). These presumptive spillover infections are believed to be incidental and not likely to result in sustained transmission in the secondarily infected species (1,3).
We conducted a survey in Death Valley National Park, California, USA, to document the presence and estimate the infection prevalence of hantavirus in rodents living in and around buildings within select developed areas of the park. The ultimate objective was to assess potential occupational risk to staff and incidental risk to visitors in a highly visited geographic area of the state that was previously unstudied (8,9).
Death Valley National Park is the largest national park in the contiguous 48 United States and is well known for having some of the hottest desert valleys in North America. Nearly 1 million persons visit the park each year; most visitation occurs during late autumn through mid-spring. Scotty’s Castle, located in the northeastern region of the park (37.031°N, 117.340°W, elevation 950 m), is a popular tourist attraction that has ≈100,000 visitors annually (US National Park Service, pers. comm., 2015). The attraction consists of an extensive 2-story historic villa and associated outbuildings, used as offices, residences, a visitor’s center, and storage, designed in Mission and Spanish Colonial Revival architecture. Below the villa lies a complex of service tunnels that are also included in tours. A year-round natural spring provides surface water flow for ≈0.3 km, creating an oasis in the desert.
We sampled rodents on the Scotty’s Castle grounds in March 2010, April 2011, and October 2011. During each sampling event, we placed 100 aluminum Sherman live-traps (HB Sherman Traps Inc., Tallahassee, FL, USA) throughout the compound, including the riparian zone, inside and around occupied and unoccupied buildings, and in the service tunnels below the villa. We baited traps with dry oats and peanuts, set late in the afternoon, and retrieved captured rodents the following morning. We anesthetized the rodents, then collected reproductive and morphometric data, and identified the rodents to species. We collected a minimum of 11 µL of blood from the retrobulbar sinus of each mouse for ELISA testing for SNV IgG (10); all Peromyscus spp. mice were humanely euthanized for SNV molecular testing. Blood samples and carcasses were analyzed at the California Department of Public Health Viral and Rickettsial Disease Laboratory (Richmond, CA, USA).
A total of 109 mice were captured during the 3 sampling events (300 trap nights): 100 (91.7%) P. eremicus, 5 (4.6%) P. maniculatus, and 4 (3.7%) P. crinitus. For P. eremicus mice, antibodies reactive to SNV antigen, PCR positive tissue, or both were detected in 13 (40.6%) of 32 collected in March 2010, 13 (32.5%) of 40 collected in April 2011, and 20 (71.4%) of 28 collected in October 2011. For P. maniculatus mice, antibodies reactive to SNV antigen, PCR positive tissue, or both were detected in 1 (100%) of 1 collected in March 2010, 0 (0%) of 1 collected in April 2011, and 2 (66.6%) of 3 collected in October 2011 (Table). None of the 4 P. crinitus mice tested positive for SNV antibodies or viral RNA. We compared viral RNA sequence (Gn) results for 48 P. eremicus and 1 P. maniculatus mice collected in each of the 3 collection periods to related hantaviruses and found a close consensus (>98%) to Convict Creek viruses 74 and 107 ([GenBank accession nos. L33474 and L33684) (11) (Figure).
The P. maniculatus deer mouse is recognized as the primary reservoir for SNV in the western United States. Published estimates for SNV seroprevalence are consistently higher in P. maniculatus mice than for any other Peromyscus species. Rodent hantavirus surveillance in California during 2001–2010 (7) detected the serum antibody to SNV among 14% (1,058/7,621) of deer mice statewide; concurrently, SNV seroprevalence for P. eremicus mice was significantly lower at 3.7% (102/2,723) and did not exceed this highest site-specific estimate at any individual surveillance site.
We identified serum antibodies to SNV in 40% of P. eremicus mice sampled. The consistently high seroprevalence over 3 sample periods suggests that SNV is efficiently transmitted and maintained within this population. The sequence characterization of viral RNA from seropositive P. eremicus mice further substantiates that the virus closely resembles type strains of pathogenic SNV associated with HPS.
The factors necessary to sustain a virus–reservoir relationship are both intrinsic and extrinsic. Hantaviruses are believed to have coevolved with their respective rodent hosts (1). P. eremicus mice are most closely phylogenetically related to P. maniculatus and P. leucopus mice, reservoirs for hantaviruses SNV and Monogahela virus, respectively, which are recognized to cause HPS (12). The close genetic similarity among these species may best enable P. eremicus mice among Peromyscus spp. mice in California to serve as a viable alternative host for SNV or to harbor a coevolved hantavirus of similar SNV lineage.
Hantaviruses are transmitted between rodent hosts through direct contact. Thus, a minimum population density is required to sustain transmission within an isolated group. The optimal habitat provided by the oasis setting of our study enables the typically solitary cactus mouse (13) to achieve a greater population density not generally found in most of the sylvan desert habitats where these mice are native (0.21–3.3/hectare) (14). Further studies in similar high density/optimal peridomestic habitats, which are associated with higher SNV infection prevalence (1), are needed to establish whether this high level of infection is reflective of the unique environment or an alternate phenotypic expression or strain, considering the enhanced transmission and maintenance of SNV in cactus mice detected at this location.
These findings underscore the importance of rodent exclusion and management in and around rural and semirural buildings where risk for contact between rodents and humans is high, even in the absence of P. maniculatus mice (9,15). Park leadership and staff were notified of our study results and given training on hantavirus awareness and prevention, and hantavirus pamphlets were made available for visitors to the park.
Dr. Burns is a Senior Public Health Biologist at the California Department of Public Health, Vector-Borne Disease Section, Infectious Diseases Branch, Division of Communicable Disease Control. His primary focus is the surveillance for and prevention of emerging and re-emerging vector-borne diseases in rural and semi-rural communities in the eastern Sierra and southern California.
The authors thank the staff of Death Valley National Park, in particular the staff at Scotty’s Castle, Abbey Wine, and Linda Manning, for their assistance.
This work was funded under the auspices of Cooperative Agreement H2480070003 between the National Park Service and Public Health Foundation Enterprises, a nonprofit 501c3 corporation that provides operational support to the California Department of Public Health.
Animal handling techniques were performed in accordance with guidelines of the American Society of Mammalogists for the use of wild mammals in research (https://doi.org/10.1644/10-MAMM-F-355.1).
- Mills JN, Amman BR, Glass GE. Ecology of hantaviruses and their hosts in North America. Vector Borne Zoonotic Dis. 2010;10:563–74. DOIPubMedGoogle Scholar
- Childs JE, Ksiazek TG, Spiropoulou CF, Krebs JW, Morzunov S, Maupin GO, et al. Serologic and genetic identification of Peromyscus maniculatus as the primary rodent reservoir for a new hantavirus in the southwestern United States. J Infect Dis. 1994;169:1271–80. DOIPubMedGoogle Scholar
- Jay M, Ascher MS, Chomel BB, Madon M, Sesline D, Enge BA, et al. Seroepidemiologic studies of hantavirus infection among wild rodents in California. Emerg Infect Dis. 1997;3:183–90. DOIPubMedGoogle Scholar
- Sanchez AJ, Abbott KD, Nichol ST. Genetic identification and characterization of limestone canyon virus, a unique Peromyscus-borne hantavirus. Virology. 2001;286:345–53. DOIPubMedGoogle Scholar
- Rawlings JA, Torrez-Martinez N, Neill SU, Moore GM, Hicks BN, Pichuantes S, et al. Cocirculation of multiple hantaviruses in Texas, with characterization of the small (S) genome of a previously undescribed virus of cotton rats (Sigmodon hispidus). Am J Trop Med Hyg. 1996;55:672–9. DOIPubMedGoogle Scholar
- Monroe MC, Morzunov SP, Johnson AM, Bowen MD, Artsob H, Yates T, et al. Genetic diversity and distribution of Peromyscus-borne hantaviruses in North America. Emerg Infect Dis. 1999;5:75–86. DOIPubMedGoogle Scholar
- California Department of Public Health Vector-Borne Disease Section. 2010 Annual Report [cited 1/17/2018]. http://www.cdph.ca.gov/programs/vbds/Documents/VBDSAnnualReport10.pdf
- Levine JR, Fritz CL, Novak MG. Occupational risk of exposure to rodent-borne hantavirus at US forest service facilities in California. Am J Trop Med Hyg. 2008;78:352–7.PubMedGoogle Scholar
- Eisen L, Wong D, Shelus V, Eisen RJ. What is the risk for exposure to vector-borne pathogens in United States national parks? J Med Entomol. 2013;50:221–30. DOIPubMedGoogle Scholar
- Ksiazek TG, Peters CJ, Rollin PE, Zaki S, Nichol S, Spiropoulou C, et al. Identification of a new North American hantavirus that causes acute pulmonary insufficiency. Am J Trop Med Hyg. 1995;52:117–23. DOIPubMedGoogle Scholar
- Schmaljohn AL, Li D, Negley DL, Bressler DS, Turell MJ, Korch GW, et al. Isolation and initial characterization of a newfound hantavirus from California. Virology. 1995;206:963–72. DOIPubMedGoogle Scholar
- Bradley RD, Durish ND, Rogers DS, Miller JR, Engstrom MD, Kilpatrick CW. TOWARD A MOLECULAR PHYLOGENY FOR PEROMYSCUS: EVIDENCE FROM MITOCHONDRIAL CYTOCHROME-b SEQUENCES. J Mammal. 2007;88:1146–59. DOIPubMedGoogle Scholar
- MacMillen RE. Population ecology, water relations, and social behavior of a southern California semidesert rodent fauna. Univ Calif Publ Zool. 1964;71:1–59.
- Chew RM, Chew AE. Energy relationships of the mammals of a desert shrub (Larrea tridentate) community. Ecol Monogr. 1970;40:1–21. DOIGoogle Scholar
- Núñez JJ, Fritz CL, Knust B, Buttke D, Enge B, Novak MG, et al.; Yosemite Hantavirus Outbreak Investigation Team. Hantavirus infections among overnight visitors to Yosemite National Park, California, USA, 2012. Emerg Infect Dis. 2014;20:386–93. DOIPubMedGoogle Scholar
TableCite This Article
Original Publication Date: May 04, 2018
1These authors contributed equally to this article.
Table of Contents – Volume 24, Number 6—June 2018
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Please use the form below to submit correspondence to the authors or contact them at the following address:
Joseph E. Burns, California Department of Public Health, Vector-Borne Disease Section, 2151 E Convention Center Way, Ste 218B, Ontario, CA 91764, USA