- Letter to the Editor
- Open Access
Prevalence of Borrelia burgdorferi-infected ticks from wildlife hosts, a response to Norris et al.
© Esteve-Gassent et al.; licensee BioMed Central. 2015
- Received: 6 October 2014
- Accepted: 13 February 2015
- Published: 27 February 2015
In a recent Letter to the Editor, Norris et al. questioned the validity of some of our data reported by Feria-Arroyo et al. The main issue investigated by us was the potential impact of climate change on the probable distribution of the tick vector Ixodes scapularis in the Texas-Mexico transboundary region. As an ancillary issue, an analysis of sequence data for the intergenic spacer of Borrelia burgdorferi was conducted. In the present letter, we provide further evidence supporting our original results, and advocate that extensive study of the population genetics of B. burgdorferi is needed in the Texas-Mexico transboundary region.
- Lyme Disease
- Borrelia Burgdorferi
- Tick Vector
- Questing Tick
- Questing Nymph
We begin addressing the criticism expressed by Norris et al.  that our intergenic spacer (IGS) data for Borrelia burgdorferi sensu stricto sequences does not support the claim of B. burgdorferi tick infection rates in Texas and northeastern Mexico. First and foremost, perspectives like the one presented in our publication can help address the gap in knowledge of Lyme disease (LD) considering that its geographical area is expected to spread in the coming years . Norris et al.  do not seem to dispute that we found B. burgdorferi in the I. scapularis collected in Texas and Mexico, but seem to question the tick infection rates reported. In their criticism Norris et al.  failed to relate our collective findings based on eco-epidemiological data documenting a continuum in the pathogenic landscape of LD in the Texas-Mexico transboundary region. In addition, members of our international research group collected nymph and adult I. scapularis from wild mammals in forest zones at an altitude of 1600–2670 meters above the sea level in the Mexican state of Nuevo León. This allowed us to state that northeastern Mexico meets ecological criteria to be considered endemic for LD .
The most relevant issue addressed by Feria-Arroyo et al.  consists of the potential impact of climate change in the distribution model of the tick vector I. scapularis in the Texas-Mexico transboundary region, based on present predictions of suitable habitat, as well as forecasting to year 2050. The major motivation of this study was the need to generate a current distribution model for this tick vector, together with future distribution models that forecast any changes under different climate change scenarios. These efforts will serve to increase our knowledge of the ecology of B. burgdorferi and its interaction with the competent vector I. scapularis in Southern US, where the incidence of LD in humans is very low. Norris et al.  disagree with the levels of B. burgdorferi infection that we detected on I. scapularis collected from non-human mammal hosts, although they do concur that B. burgdorferi infection does occur in Texas (http://www.cdc.gov/lyme/stats/). The evidence used by Norris et al. , to question our findings is based on data obtained by Williamson et al. . Because the ticks on Williamson et al. study were obtained from humans in a passive surveillance setting, we do not consider a comparison of Williamson et al.  data and ours appropriate. Contrary to what Norris and collaborators wrongly state in their letter, our paper reported B. burgdorferi infection levels in ticks exclusively found in non-human-hosts or questing on vegetation. The Feria-Arroyo et al. report does not include any ticks recovered from humans. It is highly possible that infection levels on non-human hosts differ from infection levels detected in humans, thus making both datasets not comparable.
Also, Norris et al.  affirm that “tick stage was not reported” for our collections, but this information is addressed extensively in page 12, paragraph 2, where collected adult ticks are described. Furthermore, they assert that infection prevalence in these ticks removed from animal hosts would likely be different from that of questing nymphs that are more likely to infect humans, further supporting our argument for the incompatibility of contrasting these two datasets, ours and the one in Williamson et al. . It is worth mentioning that Norris et al.  close that paragraph stating that our study “as designed, would not provide a clear-cut indication of the human risk for Lyme disease”, thus implying a goal that was never mentioned in the Feria-Arroyo et al.  paper. Nowhere in our paper do we address human risk for LD in the Texas-Mexico transboundary region, nor do we make any implications or conclusions in that direction. Our main model results are restricted to a predicted distribution for I. scapularis, which is based on a presence-absence model with no assumptions being made on the density of the different tick life stages. Moreover, we clearly indicate the need for further comparative studies to better understand LD in different ecological regions.
Taken together all the analyses generated throughout our studies, and previous studies with human isolates of B. burgdorferi sensu stricto from Texas , suggest little genetic variability in the markers analyzed (flaB and IGS) and support the fact that contamination during the testing process was unlikely. The flaB sequences reported in this letter have been published in GenBank (NCBI National Center of Biotechnology Information, accession numbers KM875668 through KM875675, http://www.ncbi.nlm.nih.gov/genbank/).
Norris et al. stated in their letter that due to the low variability observed in the IGS from the Texas samples most, if not all of them, were likely to have been originated from the same clone which they assume could be the product of contamination with the B31 strain. We disagree with the interpretation put forward by Norris et al. and instead think it is more likely that the lack of variability reported in Feria-Arroyo et al. reflects the level of B. burgdorferi variability present in the Texas-Mexico transboundary region. Several of the ticks included in the Feria-Arroyo study were collected from white-tailed deer, gemsbok and dog. These mammalian hosts, particularly white-tailed deer, harbour ticks from several lineages. Thus, ticks collected from white-tailed deer, even if collected from the same individual, are likely to carry a representation of the B. burgdorferi strains present in a particular location. Thus, the B. burgdorferi genetic diversity reported by Feria-Arroyo et al., likely represents the genetic variation present in the Texas-Mexico transboundary region. Interestingly, our host-seeking (i.e., questing) ticks found on vegetation (i.e., BWTX12-14, 17 and 24) show more genetic variation than samples collected from white-tailed deer and gemsbok, yet samples from questing ticks in the Texas-Mexico transboundary region show still lower variability than what has been reported in the US Northeast and Midwest .
The lack of variation in the IGS and flaB B. burgdorferi sequences may reflect the fact that low genetic variation of B. burgdorferi is present on ticks feeding on non-human hosts in the Texas-Mexico transboundary region sampled areas. It is not uncommon for bacteria to show different levels of genetic variation at different geographic locations [14,15]. Variation in sequence diversity among different geographic regions can be explained by different selection regimes, local adaptation, recent colonization events, and/or genetic drift. Currently several ecological factors associated with LD transmission in the Texas-Mexico transboundary region are unknown. Without further research on the ecology of competent and potential vectors and hosts, it is difficult to pinpoint the reasons for the variability observed in IGS and flaB sequences with a high degree of accuracy. The fact that B. burgdorferi sequences differ widely in genetic diversity between B. burgdorferi samples collected from ticks feeding on non-human and human-hosts from different regions is a clear indication that this needs further research. Although this was not the main topic of our paper we conclude that additional studies should explore the reasons explaining the observed IGS and flaB B. burgdorferi sequence homogeneity in the Texas-Mexico transboundary region [4,7] as compared with what has been observed in the Northeastern and Midwestern US.
Our team supports the fact that Texas is a low incidence state for human cases of LD [16-19]; however, the ecology of this disease in the Texas-Mexico transboundary region is understudied. Given that this region is a completely different environment, as compared to Northeastern and Midwestern US, it is highly likely that LD ecology will follow a different dynamic. Variation in tick ecology, tick questing behaviour, and vertebrate host communities between these regions that have considerable differences in climate, species diversity and composition, are likely to influence the ecology of LD as well as its transmission potential to humans. Thus, extrapolations based on findings from the Northeastern and Midwestern US may not be accurate enough to understand LD transmission and ecology in other regions. Our research team is interested in elucidating the ecological factors that explain the low human infection incidence reported in the southern US and northern Mexico to better understand the dynamics of this tick borne disease across its distribution range.
Norris et al. suggest that the Feria-Arroyo et al.  publication is advocating a high LD risk in Texas and Mexico but this cannot be further from the truth. Unlike publications that have aimed to create disease risk maps based on questing infected nymphs [16,17,19] the Feria-Arroyo et al.  presents a habitat suitability model for the presence of the vector in the studied area, and no predictions are made in regards to the density and prevalence of infected ticks. We agree with Norris et al. that it is unfortunate that the “Feria-Arroyo et al.  has been publicised as an indication of a significant Lyme disease risk in Texas” but misinterpretations of that paper in media outlets are not the responsibility of the authors. Throughout the Discussion section of Feria-Arroyo et al.  it is stressed that a direct correlation between vector presence and human disease cannot be made because of the lack of knowledge about the disease ecology for this pathogen in the studied region.
Norris et al. go a step further and even ask for the paper to be removed from the literature, but we claim this move is unwarranted for two main reasons. First, it will be naïve to think that a whole public health strategy will be swayed based on a study that does not address human risk for the disease. Secondly, the main findings of the Feria-Arroyo et al. paper , which are the vector distribution models, remain unchanged independently of the disputed B. burgdorferi prevalence rates. Removing the contribution of these vector distribution models from the literature would be a step backwards for the continued study of tick-borne illnesses in the southern United States, a goal that we agree with Norris et al. is worthy of further academic work.
MDEG has obtained support for this study through the Department of Veterinary Pathobiology, Texas A&M University, AgriLife grant TEXV 6579 (Project I-9524). USDA is an equal opportunity provider and employer.
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