In recent years, Pennsylvania has led the United States in number of Lyme disease cases [1,11]. Because of human population density and proximity to the heavily populated areas of the northeastern U.S., there is a continuing misconception that Lyme disease cases are on the rise only in northeast Pennsylvania [12]. But over the past decade, many counties in western Pennsylvania have experienced an increase in incidence of Lyme Borreliosis in human adults and children [11] which is corroborated by the latest CDC finding that "The center of the high-incidence focus in the northeastern United States generally moved westward and northward, away from the coast of northern New Jersey and into east-central Pennsylvania" [13].
A combination of varying land use practices, diverse and abundant wildlife reservoirs (white-footed mouse, white-tailed deer, ground birds, eastern chipmunks, shrews), and recreational activities such as hiking, camping, fishing and hunting have increased the potential exposure of humans to I. scapularis ticks in western Pennsylvania. It is estimated that Pennsylvania's public recreational areas attract over 34 million visitors annually [14] and Pennsylvania ranks sixth in yearly sales of fishing licenses and second in yearly sales of hunting licenses [15]. Thus, the Commonwealth of Pennsylvania hosts a large human demographic that is at risk for exposure to multiple tick-borne pathogens.
The purpose of this study was to determine (i) the infection rates for A. phagocytophilum, B. microti and B. burgdorferi in I. scapularis collected in recreational areas of a western Pennsylvania county known to have a high-incidence for human Lyme disease; and (ii) the frequency of co-infections in these ticks which could translate to concurrent infections in humans via a single tick bite. Our results have added to the knowledge of the microbial community residing in I. scapularis ticks in hot spot areas, which is important for increasing human vigilance and for public health professionals to make more informed prevention, diagnoses, and treatment decisions.
All ticks were collected by dragging a white cloth attached to a rope through vegetation and leaf litter along hiking trails and in adjacent forests. All ticks collected were immediately transferred to 70% ethanol and stored in a laboratory at the Indiana University of Pennsylvania (IUP, Indiana, Pennsylvania) until experimentation. Prior to pathogen testing, adult I.scapularis ticks were identified as either male or female based on morphological differences [16].
To detect A. phagocytophilum, we used the ge3a-F/ ge10r-R primer set (GenBank accession number KJ942183.1). The forward primer was 5' CAC ATG CAA GTC GAA CGG ATT C 3' and the reverse primer were 5' TTC CGT TAA GAA GGA TCT AAT CTC C 3' amplifying a 932-base pair (bp) product specific for the A. phagocytophilum 16S rRNA gene. Amplification was performed as follows: 3 min at 98°C (one cycle) followed by 40 cycles for 5 sec at 98°C, 5 sec at 55°C, 90 sec at 72°C. A. phagocytophilum was not further differentiated between the human pathogenic (APHa) and the nonpathogenic (AP-variant 1) strains [12].
We used the PIRO-AF/ PIRO-BR primer set to detect B. microti [17]. The forward primer was 5' ATT ACC CAA TCC TGA CAC AGG G 3' and the reverse primer was 5' TTA AAT ACG AAT GCC CCC ACC 3' amplifying a 437-bp product specific for the B. microti 18S rRNA gene. Amplification was performed as follows: 3 min at 98°C (one cycle) followed by 40 cycles for 5 sec at 98°C, 5 sec at 55°C, 30 sec at 72°C.
To detect B. burgdorferi, we used the FL6-F/ FL7-R primer set (GenBank accession number X63413.1). The forward primer was 5' TTC AGG GTC TCA AGC GTC TTG GAC T 3' and the reverse primer were 5' GCA TTT TCA ATT TTA GCA AGT GAT G 3' amplifying a 276-bp product specific for the B. burgdorferi flagellin gene [18]. Amplification was performed as follows: 3 min at 98°C (one cycle) followed by 40 cycles for 5 sec at 98°C, 5 sec at 55°C, 30 sec at 72°C.
To confirm that all PCR reactions had I. scapularis tick DNA, we amplified the 16S rRNA gene of I. scapularis tick using the Iscap16SF/Iscap16SR primer set (Genbank accession number KF146646). The forward primer was 5' CGG TCT GAA CTC AGA TCA AG 3' and the reverse primer was 5' GGG ACA AGA AGA CCC TAT G 3' amplifying a 320-bp product specific for the 16S rRNA gene of the I. scapularis tick.
All PCR products were separated by horizontal gel electrophoresis on a 1.2% Tris-acetate EDTA (TAE) ethidium bromide agarose gel followed by analyses using a Gel Doc XR Imager (Bio-Rad, Hercules, CA).
The three pathogens were relatively independent in their distribution among ticks, both in the actual combinations of
Pathogens in I. scapularis |
total |
M |
F |
M vs F |
|||||
n |
rate |
n |
rate |
n |
rate |
Chi square |
df |
p |
|
B. burgdorferi |
76 |
0.302 |
23 |
0.232 |
53 |
0.346 |
3.71 |
1 |
0.054 |
B. microti |
69 |
0.274 |
29 |
0.293 |
40 |
0.261 |
0.30 |
1 |
0.584 |
A. phagocytophilum |
9 |
0.036 |
1 |
0.010 |
8 |
0.052 |
3.11 |
1 |
0.078 |
no pathogens |
124 |
0.492 |
53 |
0.535 |
71 |
0.464 |
2.36 |
2 |
0.307 |
only 1 pathogen |
105 |
0.417 |
40 |
0.404 |
65 |
0.425 |
|||
more than 1 pathogen |
23 |
0.091 |
6 |
0.061 |
17 |
0.111 |
|||
at least 1 pathogen |
128 |
0.508 |
46 |
0.465 |
82 |
0.536 |
1.22 |
1 |
0.269 |
Pathogens in I. scapularis |
Observed |
Expected |
Observed vs. expected |
||||
(n) |
rate |
(n) |
rate |
Chi square |
df |
p |
|
B. burgdorferi(Bb) |
76 |
0.302 |
-- |
-- |
-- |
-- |
-- |
B. microti (Bm) |
69 |
0.274 |
-- |
-- |
|||
A. phagocytophilum(Ap) |
9 |
0.036 |
-- |
-- |
|||
Bb + Bm |
16 |
0.063 |
20.81 |
0.083 |
2.36 |
3 |
0.501 |
Bb + Ap |
3 |
0.012 |
2.71 |
0.011 |
|||
Bm + Ap |
1 |
0.004 |
2.46 |
0.010 |
|||
Bb + Bm + Ap |
3 |
0.012 |
0.74 |
0.003 |
|||
no pathogens |
124 |
0.492 |
123.24 |
0.489 |
0.33 |
2 |
0.850 |
only 1 pathogen |
105 |
0.417 |
102.02 |
0.405 |
|||
more than 1 pathogen |
23 |
0.091 |
26.73 |
0.106 |
|||
at least 1 pathogen |
128 |
0.508 |
128.76 |
0.511 |
-- |
-- |
-- |
Nine percent of the ticks sampled were co-infected with more than one pathogen which is not surprising given that zoonotic pathogens share a common I. scapularis tick vector and small mammal reservoirs [4-6]. We saw no evidence that coinfection occurred more or less often than expected based upon the co-infections predicted by combinations of the pathogens independent frequencies. Our coinfection rates for B. burgdorferi + A. phagocytophilum and B. microti+ A. phagocytophilum were similar to a prior study conducted in southwestern Pennsylvania [18]. In spite of these three pathogens potentially sharing some common animal reservoirs, we found B. burgdorferi to have an uneven distribution (independent of sample size) among the nine recreational areas we sampled which could be due to differences in prevalence of hosts these ticks feed on during the larvael or nymphal stages of their development [10]. Additionally, the number and/or source of blood meals, and thus the opportunity for infection, could possibly be the reason for marginal differences in B. burgdorferi (p = 0.054) and A. phagocytophilum (p = 0.078) prevalence between male and female ticks [10]. The 27% prevalence rate for B. microti in this study could be attributed to regional variation [20] and sampling of I. scapularis ticks for microbial pathogens in a high incidence southwestern Pennsylvania county compared to prior studies which sampled ticks from random locations in western Pennsylvania [18,19,21]. In support of our findings, a study by Piesman, et al. [22] demonstrated the wide prevalence of B. microti (2%-47%) in adult I. scapularis from four areas in eastern Massachusetts.
Although the biotic and abiotic factors influencing the distribution of I. scapularis ticks and their transmission of the zoonotic pathogens they carry are complex [23] and beyond the scope of this manuscript, it is obvious that Lyme disease in southwest Pennsylvania is on the rise [11,13]. During a five year period (2010-2014), Pennsylvania Department of Health [11] reported a seven fold increase in Lyme disease incidence rate in southwest Pennsylvania (75.72 in 2014 versus 11.5/100,000 persons in 2010) as compared to a two-fold increase in northeast Pennsylvania (54.4 in 2014 versus 30.51 in 2010), which the CDC have corroborated in their recent findings [13].
It has been previously reported that human Lyme and Babesiosis are commonly diagnosed in overlapping geographic areas, especially in regions with high human densities of the northeast (New York, New Jersey) and Midwest (Minnesota, Wisconsin) United States [24]. To date, the human incidence rate for Anaplasmosis and Babesiosis for Pennsylvania is not reported by CDC. But, given our findings and the high incidence rates for Anaplasmosis and Babesiosis in states bordering Pennsylvania (New York and New Jersey) [1], human infection by one of these two emerging blood-borne pathogens is possible via a single I. scapularis tick bite [25] which could result in concurrent infections and contribute to a variety of clinical symptoms not typically seen in Lyme disease patients.
Due to current observed changes in the seasonal and environmental landscape of our planet, the upward trend in I. scapularis tick population size and co-infection rates with the zoonotic pathogens is likely to continue [2]. Although factors affecting tick coinfection and risks posed to humans need further study, it is warranted that the scientific community, public health officials, and health care providers, think beyond Lyme so as to be unbiased in their diagnosis of other emerging tick-borne diseases as well as co-infection complications that could result from a single I. scapularis tick bite. We also urge managers and public users of recreational areas to be aware of the risks of coinfections and become more familiar with tick prevention measures and symptoms of these emerging tick-borne diseases.
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