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Journal of Microbiology and Modern Techniques
ISSN: 2575-5498
United States Air Force Academy: Identifying Areas at Risk for the Persistence of Plague using the Bioagent Transport and Environmental Modeling System (BioTEMS)
Copyright: © 2017 Thomas M Kollars. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
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Introduction: Yersinia pestis, the etiologic agent of plague, has caused major pandemics in human history and continues to be both a natural and bioterrorist threat to human populations. Plague exists in nature in either an epidemic or enzootic state. Geographic models of the epidemic state have primarily been developed using flea and reservoir species, however little is known of the enzootic state and potential cryptic reservoir species and few endemic models have been produced.
Methods: Flora, fauna, soil data were analyzed using geographic information systems and the Bio agent and Environmental Transport System Model (BioTEMS). BioTEMS has been used to evaluate and model several pathogens globally.
Objective: BioTEMS is used in the present study to identify likely sites for enzootic transmission and cryptic species of Y. pestis to enhance surveillance and control of plague by public health professionals at the United States Air Force Military Academy.
Results: One hundred fifty-five sites were identified as being at risk of high persistence of plague. Eight sites were within 250 meters of base housing and could serve as sources for infecting fleas, rodents and human infection. A significant number of black-tailed prairie dog mounds were within 250 meters of HPP sites, 52 of 67, X2=40.9, p<0.01.
Conclusion: Areas at risk of persistence of Yersinia pestis, the etiologic agent of plague were identified at the United States Air Force Academy using the Bio agent Transport and Environmental Modeling System. Several of these sites were near base family housing and near prairie dog mounds. This information can be used by public health officials to optimize vector/rodent control and to conduct environmental surveillance to reduce the risk of outbreaks of plague on the academy property.
Keywords: Yersinia pestis; Epidemiology; Terrorism GIS; Infectious disease; Microbial ecology; Free-living pathogenic amoeba
Yersinia pestis, the etiologic agent of plague, has caused three pandemics, and continues to be a threat to human populations across the globe as a naturally occurring organism and as a potential biological weapon. The most common methods of humans becoming infected is through the bite of a flea infected by feeding upon a rodent reservoir or by the person handling an infected carcass. Currently, more than 200 species of animals and 80 species of fleas have been implicated in maintaining Y. pestis endemic foci throughout the world [1]. Plague was first introduced to North America in the 19th century and is now endemic from California eastward to the eastern slope of the United States [2]. Yersinia pestis exists as either an enzootic in a resistant host population or in an epizootic state in susceptible hosts [3].
Both plague infected animals and human cases have been reported on the United States Air Force Academy Base (AFA), located in Colorado [4]. The AFA is composed of nearly 8,000 ha located in El Paso County on the eastern slope of the Rocky Mountains. Children have died in family housing, where infected rodents and their associated fleas have been found [4]. Determining where plague is present on the AFA is important not only in preventing plague in cadets and staff at the academy, but also military personnel and their families occupying family housing at the installation. Current models have low spatial accuracy for identifying epizootic activity prior to human plague cases suggesting other mammalian reservoirs or their fleas may be more important sources in high risk areas, e.g. chipmunks, however several models have been used with increasing resolution to within 30 to 100 m [5]. In addition to mammalian reservoirs and flea species, microbial communities and environmental factors may play a role in identifying high risk areas for plague at the AFA. The objective of this study was to identify high risk areas of persistence of Y. pestis at the AFA to assist in plague surveillance and prevention, and identify if enzootic persistence may be located near base housing utilizing the Bioagent Transport and Environmental modeling system (BioTEMS).
Flora, fauna, soil data were obtained from the Natural Resources Department (AFA) and the United States Geological Service (USGS). Soil samples and observations of ground squirrels and prairie dog communities were recorded and GPS referenced. Neural network analysis of microbial density, measured by Luminultra test kits, from soil samples sampled in Colorado and Montana were utilized for characterization of microbial microhabitat (Figure 1). ArcGIS geospatial analysis software, Statistica software and the BioTEMS were used to analyze geographic information and conduct data analysis to identify likely areas of persistence of Y. pestis. The BioTEMS has previously been used for biological weapons defense modeling and infectious disease modeling in several countries, including plague [6]. The BioTEMS utilizes up to several hundred abiotic and biotic factors to produce risk and vulnerability assessments for biological agents and infectious diseases. Examples of biotic and abiotic factors include; pathogen strain, vector/host relationship, vectorial capacity, host/vector physiology, colonization ability, population dynamics of hosts and vectors, microbial density, soil, shade, and weather conditions, such as wind, temperature, and precipitation. Analytical methods within BioTEMS include; artificial intelligence, fuzzy logic, and niche analysis.
One hundred fifty-five sites were identified as being at risk of high persistence of plague (HPP) (Figure 2). Eight HPP were within 250 meters of base housing and could serve as sources for infecting fleas, rodents and human infection. A significant number of black-tailed prairie dog mounds were within 250 meters of HPP sites, 52 of 67, X2=40.9, p<0.01. This is within the range of dispersion by other rodents, e.g. spotted ground squirrels [7] and could be a source of infection for prairie dogs. Black-tailed prairie dogs are an important species for plague surveillance; however resources should also be directed towards other possible hosts and evaluating human risk by incorporating fluctuations in levels of endemic and epidemic risk [5]. Adding potential interactions with microbial hosts and microhabitats can increase the resolution of the model and provide a preventive model with reduced cost.
Enzootic models have been used to identify probable reservoir and flea species where enzootic and non-peridomestic plague continues between epizootic outbreaks [5]. The potential distribution of flea vectors of Y. pestis in California has provided assistance in focusing sampling of plague vectors [8]. In addition to flea vectors and mammalian reservoirs, soil and microbial communities appear to play a role in enzootic maintenance of Y. pestis, including free-living amoeba [9-14]. Models of human associated plague using environmental and host factors have been used to assist in prevention of plague from epizootics in four southwest states, including Colorado [15-17]. However, these models do not include potential Y. pestis interactions in the microbial environment.
Free-living amoeba, provide a macrophage-like environment and serve as suitable hosts for several human pathogens. Pathogenic bacteria interact with the amoebae, residing in both trophozoite and cyst forms, protected from deleterious environmental factors and even gaining pathogenicity [18]. Yersinia pestis is associated with and can persist in free-living pathogenic amoeba, e.g. Acanthamoeba castellani [13,14]. Yersinia pestis also persists in free-living pathogenic amoeba, providing prolonged survival and subversion of intracellular digestion of Y. pestis within a soil free-living amoeba. This suggests the potential role for protozoa as a protective soil reservoir for Y. pestis [19]. Mammals often come into contact with free-living amoebae but vary in susceptibility to free-living pathogenic amoeba, such as Naegleria species, can depending on species, age and sex of the host [20]. Susceptible mammals may become infected by Y. pestis when they come into contact with free-living amoeba [18].
Human cases of plague have occurred in military housing at the AFA [4]. Even though peridomestic rodent control is conducted in military housing, the death of a child in base housing at the AAF emphasizes the need to develop new strategies of surveillance and control methods in family housing in order to reduce risk to military personnel and their families. Housing areas on military bases are sometimes at high risk from vector-borne diseases, e.g. enlisted housing at Edgewood Army Base, MD was identified as being at high risk for Ixodes scapularis the tick vector of Borrelia burgdorferi, the etiologic agent of Lyme borreliosis (Kollars, unpublished). In the present study, several high risk areas for plague were identified near base housing using BioTEMS. Having the ability to prioritize likely areas and identify sites for sampling for endemic persistence of plague can reduce the manpower and logistics spent in surveillance while enhancing prevention. Current methods of plague surveillance focus on rodent and flea testing for prevention and control of plague outbreaks. Adding the testing of the soil microbial community, e.g. free-living amoebae into surveillance operations may provide valuable insight into sites identified as high persistence areas for Y. pestis and other pathogens. Niche analysis is a useful tool when identifying the potential distribution of pathogenic species and should incorporate factors in addition to geographic locality and habitat, e.g. genotypic/phenotypic diversity, host susceptibility, and potential microbial reservoirs. Strain variation of Y. pestis plays a role in host invasion and environmental survival and behavioral and physiologic condition of individuals affects susceptibility to Y. pestis [21-23].
Areas at risk of persistence of Yersinia pestis, the etiologic agent of plague were identified at the United States Air Force Academy using the Bio agent Transport and Environmental Modeling System. Several of these sites were near base family housing and near prairie dog mounds. This information can be used by public health officials to optimize vector/rodent control and to conduct environmental surveillance to reduce the risk of outbreaks of plague on the academy property.
The authors would like to express appreciation to the staff of the U.S. Air Force Academy Natural Resources Management for providing support. The authors dedicate this paper to the memory of Peggy Gardner Kollars, wife, mother, friend and scientist for helping to coordinate this study who is now in heaven with Jesus and we know we will see her again because we have faith also. The views expressed in this publication are those of the author’s and do not reflect the official policy of the United States Army or United States Government. The author reports no conflict of interest in this work.
Adenovirus (Source: CDC) Figure 1: Radial Basis Function Neural Network of predicted microbial density in microhabitats of soils within the US Air Force Military Academy; Profile: RBF 9:9-1- 1:1, Index=20 Train Perf.=0.99, Select Perf.=1.03, Test Perf.=0.90 |
(Source: Courtesy of Linda Stannard, University of Cape Town, S.A.) Figure 2: High risk areas of Yersinia pestis persistence identified using the Bio agent Transport and Environmental Modeling System |
Figure 3: Positive immunofluorescence tests for a) HSV antigen from epithelial cell b) CMV pp65 antigen from peripheral blood neutrophils and c) Test for rabies virus antigen (Source: CDC) |
Type of virus | Cell lines | |
1 | Herpes Simplex | Vero, Hep-2, human diploid (HEK-293 and HELA), human amnion |
2 | VSV | human diploid (HELA, HEK) |
3 | CMV | human diploid fibroblasts (HEF) |
4 | Adenovirus | Hep-2, HEK, |
5 | Poliovirus | MK, BGM, LLC-MK2, Vero, Hep-2, Rhadomyosarcoma, HELA, HEK |
6 | Coxsackie B | MK (Monkey Kidney cell), BGM, LLC-MK2, Vero, hep-2 |
7 | Echo | BGM (Buffalo green monkey), MK, LLC-MK2, human diploid, Rd |
8 | Influenza A | MK, LLC-MK2, MDCK(Madin-Darby canine kidney cells) |
9 | Influenza B | MK, LLC-MK2 (Rhesus Monkey Kidney Epithelial Cells), MDCK |
10 | Parainfluenza | MK, LLC-MK2 |
11 | Mumps | MK, LLC-MK2, HEK, Vero |
12 | RSV | Hep2 (Human epidermoid cancer cells), Vero |
13 | Rhinovirus | human diploid (HEK, HEL (Henrietta Lacks)) |
14 | Measles | MK, HEK(Human embryo kidney), Vero, B95a |
15 | Rubella | Vero, RK13 (Rabbit kidney epithelial cells) |
16 | Rabies | WI-38 (Human lung fibroblast cell line), human diploid cells |
17 | HCV | (Huh-7) human hepatocellular carcinoma cell line |
Table 1: Some selected viruses and their cell cultures |
Name of Virus
|
Cell Culture | Origin of cell | Specimen type | Incubation period (CPE) | Storage temperature |
CMV | HEL | Human embryonic lung fibroblasts | CSF/Blood | 5 - 14 days | -70 °C to -196 °C |
Poliovirus(1,2,3) | Rhadomyosarcoma (Rd) | Human cancer of connective tissue | Stool | 1 - 7days | -86 °C to -196 °C |
VZV | HeLa | Human fibroblasts | Vesicle fluid and scrapings | 5 - 14 days | -70 °C to -196 °C |
RSV | HeP-2 | Human cervical cancer cells | Nasopharyngeal aspirates, nasal washes | 4 - 5 days | -70 °C to -196 °C |
Influenza A | MDCK | Madin-Darby canine kidney cells | Throat swab | 2 - 5 days | -70 °C to -196 °C |
HSV | HEK-293 | Human diploid cell | Genital and tissue lesions | 1 - 4 days | -70 °C to -196 °C |
Adenovirus | HEK | Human embryo kidney | Stool/eye swab | 2 - 7 days | -80 °C to -196 °C |
Mumps | MK | Monkey kidney cell | pharyngeal exudates, saliva | 3 - 10 days | -20 °C to -70 °C |
Rubella virus | RK-13 | Rabbit kidney cell | Dermal lesion | 3 -10 days | -70 °C to -196 °C |
Measles | MK | Monkey kidney cells | Blood, throat swabs | 3 - 10 days | -70 °C to -196 °C |
Rabies | WI-38 | Human lung fibroblast | Neck skin biopsy | 5-14 days | -20 °C to -80 °C |
Rhinovirus | HeLa | Human fibroblast | Nasal swab | 4-5 days | -20 °C to -196 °C |
(Source: https://www.mayomedicallaboratories.com/.html) Table 2: Different viruses with their culture, specimen type incubation period and storage temperature |