Conceived and designed the experiments: ND MM JG FSD NB EW KK SP. Performed the experiments: ND MM JG ST LA FSD NB EW KH JF SP JV TS BH CE AB PS CG HB RM JHM. Analyzed the data: ND ST LA FSD. Wrote the paper: ND MM JG ST LA FSD NB EW KH JF KK SP JV TS BH CE AB PS CG HB RH VW RM JHM.
Rocky Mountain spotted fever (RMSF) transmitted by the brown dog tick (
Rocky Mountain spotted fever (RMSF) is a severe and potentially fatal tickborne disease caused by the bacterium
The dry, hot Arizona weather is inhospitable to the temperature and humidity requirements of
Following epidemiologic and ecologic investigations, the dramatic increase in autochthonous RMSF cases in Arizona was linked to transmission by the brown dog tick
In regions where RMSF is primarily associated with
In order to determine if brown dog tick control could be attained in a heavily infested community, we designed and evaluated an intervention aimed at killing ticks on dogs and in the peridomestic environment using properly timed environmental acaricide application and long-acting tick collars for dogs.
The pilot tick prevention project, called the RMSF Rodeo, was conducted on Reservation B in Arizona, which is home to ∼10,000 individuals. This reservation is principally located in a high altitude desert zone receiving less than 18 inches of precipitation annually
The community within Reservation B that was selected for participation in the RMSF Rodeo had been highly impacted by RMSF, including two fatalities that occurred just prior to the start of the project. The community contained ∼600 (581 in 2012 and 571 in 2013) occupied homes, and was geographically isolated from other neighborhoods by open desert, roads, and a river basin.
The RMSF Rodeo was piloted to assess the efficacy of properly timed environmental acaricide treatment of home sites, treatment of dogs with long-acting tick collars, and improved access to pet care practices (tethering, spay/neuter). The program was designed to have repeated contact with participating households and dogs during times of peak tick activity in order to ensure that there were no lapses in environmental or veterinary treatments.
RMSF Rodeo activities were conducted April 2012 – September 2013 and consisted of two distinct phases. Phase 1 (April–August 2012) focused on immediate control of ticks, including:
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Phase 2 of the RMSF Rodeo (March–September 2013) focused on sustained control of ticks, consisting of:
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Between Phase 1 and Phase 2 of the RMSF Rodeo (September 2012 – March 2013), there were no formal Rodeo project activities, although the tribe continued to distribute Zodiac tick collars and treat homes upon request. Throughout the two years, the tribal animal control program increased capacity to collect and remove stray dogs across the reservation. Education about tick control and RMSF prevention were emphasized to all communities, although the RMSF Rodeo allowed for more frequent interaction with homeowners. Team members responsible for acaricide application, dog collaring and tick assessments were trained prior to each interaction to limit the amount of inter-operator variability. Teams typically consisted of 15 members (range 12–25), with 2–3 people at each location, roughly equating to ∼10,000 person-hours in the field in 2012 and 2013 (not including day-to-day animal control practices). Data associated with the routine monitoring of the dogs in both phases of the project were recorded on paper registers and were entered into Microsoft Excel databases following each visit.
Five homes within the RMSF Rodeo community were followed throughout the project to monitor tick burden in the environment. Carbon dioxide (CO2) tick traps, consisting of a 36 inch by 36 inch square of white flannel were placed in three locations at each of the five homes. These traps were set once a month from May through August in Phase 1, and in March and May of Phase 2, but were discontinued thereafter. Tick traps were collected after 4 hours. The trapped ticks were killed by freezing, sent to the medical entomology laboratory, where they were characterized as
Dogs registered in the RMSF Rodeo were tagged at registration to validate their participation and provide a means of identification. Dogs that could be caught and examined (both restrained and free-roaming dogs) were checked on a monthly basis in Phase 1 and bimonthly in Phase 2 for maintenance of their tick collar and visual tick inspections throughout the program. Dogs were examined for ticks on the ears, face, and between the toes. Visual tick inspections were categorized as: A. zero ticks visible, B. 1–20 ticks visible and C.>20 ticks visible.
At the end of each phase of the project (August 2012 and September 2013), systematic evaluations were performed to compare tick levels in both RMSF Rodeo and Non-Rodeo communities on Reservation B, and to compare practices surrounding RMSF prevention and tick control. During 2013, a reservation-wide tick prevention program was implemented in the Non-Rodeo areas, so End-of-Phase 2 evaluation results are more limited in scope and evaluations of RMSF Rodeo success are best compared with the Non-Rodeo areas in 2012 (when no intervention was applied).
To assess the effectiveness of the project and identify possible interventions according to respondents, the Rodeo community and three Non-Rodeo communities were surveyed about knowledge, attitudes, and practices surrounding RMSF, dog ownership, and animal control. Households were stratified by neighborhood, and a proportionate stratified sample of households was drawn without replacement. Households in Non-Rodeo communities were over-sampled in anticipation of lower participation. Teams travelled house-to-house administering a questionnaire to any adult member of the household who consented to participate. Electronic questionnaires were designed and data were compiled using MR Interviewer software version 5.6
Data were analyzed using SAS version 9.3
Human cases of RMSF meeting a confirmed or probable case definition are reported to the Arizona Department of Health Services (ADHS) annually
Approval for this prevention project was obtained from the Reservation B tribal council by CDC prior to the start of activities in 2012. End-of-Phase surveys were reviewed by the CDC Human Subjects Protection Office and were deemed exempt from CDC Institutional Review Board on a non-research basis. All individuals interviewed were at least 18 years of age and the survey posed minimal risk to participants. Written informed consent was obtained from all participants and no personally identifiable information was tied to survey responses.
Within the RMSF Rodeo community, 98% (576/582) of occupied households in 2012, and 99% (558/571) of occupied households in 2013 participated in the intervention project. Although defining a precise number of dogs was difficult due to births, deaths, loss, and transfer of ownership; we estimate that roughly 1000 dogs were managed within the RMSF Rodeo community each year, but that number fluctuated by month.
Substantial numbers of ticks were captured in the CO2 tick traps in May 2012 (n = 1274). Tick numbers decreased drastically in June (n = 54), with continuing decreases in the months to follow; no ticks were observed in environmental traps by the end of Phase 1 (
Dogs belonging to households participating in the RMSF Rodeo were monitored over time for visible tick infestations. Each data point represents a cross-sectional assessment of observed ticks on dogs in the project area, as not all dogs were seen during every visit. Fifty-one percent of registered dogs had visible tick infestations at the start of the RMSF Rodeo in April 2012; this decreased to <4% of dogs with ticks visible in August 2012 (
End-of-Phase evaluations allowed for the comparison of RMSF Rodeo and Non-Rodeo communities using data from households participating in the survey. Selected characteristics of these populations can be seen in
| Non-Rodeo 2012 | Rodeo 2012 | Rodeo 2013 | |
| 45.2% (39, 51) | 62.6% (56, 69) | 51.9% (45, 59) | |
| 19.2% (14, 24) | 15.2% (10, 20) | 14.8% (10, 20) | |
| 43.1% (37, 49) | 54.2% (47, 61) | 51.3% (45, 58) | |
| 37.8% (32, 44) | 29.5% (23, 36) | 33.9% (28, 40) | |
| mean = 1.6 (range 0–13) | mean = 1.8 (range 0–10) | mean = 1.8 (range 0–13) | |
| mean = 2.0 (range 0–8) | mean = 2.2 (range 0–10) | mean = 2.2 (range 0–9) | |
| 234/315 (74%) | 192/280 (69%) | 199/280 (71%) | |
| 28.3% (21, 35) | 38.9% (30, 48) | 30.0% (23, 37) | |
| 26.7% (20, 34) | 34.9% (27, 43) | 41.5% (34, 49) | |
| 45.0% (37, 53) | 26.2% (19, 34) | 28.5% (21, 36) | |
| 24.8% (21,33) | 25.5% (18, 33) | 23.1% (16, 31) | |
| 36.8% (29, 45) | 39.6% (32, 47) | 49.3% (43, 56) | |
| 38.5% (33,44) | 34.9% (29, 40) | 27.6% (22, 33) | |
| 11.4% (6,18) | 30.5% (26, 39) | NA | |
| 24.7% (17, 36) | 41% (33, 52) | NA | |
| NA | NA | 31.9% (25, 39) | |
| 79.4% (74, 85) | 79.5% (73, 86) | 84.4% (79, 90) |
Reported as weighted percent frequency (95% confidence interval), unless otherwise indicated.
Visible tick counts on dogs were also observed among surveyed households with dogs, and can be compared between RMSF Rodeo and Non-Rodeo communities (
| 2012 | 2013 | ||
| Non-Rodeo | Rodeo | Rodeo | |
| 36.1% (28, 44) | 99.2% (98, 100) | 97.7% (95, 100) | |
| 32.2% (24, 40) | 0.8% (0, 2) | 2.4% (0, 5) | |
| > | 31.7% (24, 40) | 0% | 0% |
Reported as weighted percent frequency (95% confidence interval).
The End-of-Phase evaluations also collected homeowner reports of ticks inside their house (domestic) or in their yard (peridomestic) (
In order to address factors associated with observed tick activity, a sub-analysis was performed of households in 2013 owning at least one dog (
| Dogs with ticks | Dogs without ticks | Risk ratio (95% CI) | |
| 85.5% (73, 98) | 42.5% (34, 51) | 5.4 (4.0, 7.5) | |
| 15.5% (2, 27) | 57.5% (49, 66) | ref | |
| 46.3% (28, 65) | 32.1% (25, 40) | 1.6 (1.3, 2.0) | |
| 53.7% (35, 72) | 67.9% (60, 75) | ref | |
| 19.2% (5, 34) | 36.1% (28, 44) | 0.55 (0.40, 0.74) | |
| 41.8% (23, 60) | 28.8% (21, 36) | 1.2 (0.97, 1.5) | |
| 38.9% (21, 57) | 35.2% (28, 43) | ref |
*This analysis only relates to homes with at least one dog.
Of reported human cases of RMSF on Reservation B, 62% of the cases in this four-year span met a probable case definition and 38% were considered confirmed. Average annual incidence of human cases of RMSF was estimated to be 1.2 cases per 1000 persons in both the RMSF Rodeo community and in the Non-Rodeo communities prior to the start of the RMSF Rodeo in April of 2012. In the two years following, average incidence in the RMSF Rodeo community decreased by 43% to 0.71 cases per 1000 persons. Cases also decreased in the Non-Rodeo communities, to 0.90 cases per 1000 persons, a decrease of 27% (see
The RMSF Rodeo tick prevention project successfully decreased tick levels within this tribal community, and maintained low levels of ticks for a period of at least two years. In the first year, environmental tick control methods combined with long-acting tick collars on dogs produced substantially fewer domestic and peridomestic infestations in the RMSF Rodeo community compared to the Non-Rodeo communities, as evidenced by observed tick activity on dogs, environmental CO2 traps, and homeowner reports of sighted tick activity. Once tick control had been achieved during Phase 1 of the RMSF Rodeo, using the combined environmental and veterinary tick control, tick populations were sustained at very low levels during Phase 2 of the RMSF Rodeo using tick long-acting collars alone.
We believe that the success of the RMSF Rodeo was due to the tailoring of interventions around this tick vector and its particular habits. The start of the project in March-April of each year was timed to correspond with human RMSF surveillance data showing increased cases during those months, presumably due to increased tick activity
Another important factor in the success of the project was the strong degree of support for the RMSF Rodeo within the community, as demonstrated by the high rate of household enrollment. Households were visited multiple times and registration was repeatedly encouraged in order to procure this high rate of participation, which was crucial in the project's ultimate success.
The finding that ticks were controlled across the community during Phase 2 of the project using tick collars alone is very promising. Even though Phase 2 of the project included a contingency for acaricide treatment in the project area for households where tick activity was observed, this was necessary in <5% of households in the RMSF Rodeo community, suggesting that the tick collar alone was sufficient in preventing the majority of visible tick infestations on dogs once environmental burden was reduced. This method enables more targeted and cost-efficient strategies of tick control, interceding on the primary host, and will reduce the amount of pesticides necessary in the environment.
The RMSF Rodeo project did not evaluate the efficacy of a tick collar alone during Phase 1 of the project, and we do not recommend this option for communities with high environmental tick loads. We believe rapid and immediate killing of ticks in the environment is essential to reduce RMSF risks in highly impacted communities. There is also a possible risk: if collars are used without controlling ticks in the peridomestic environment, meal-seeking ticks may be inclined to parasitize other unprotected animals in the immediate area including humans. Thus, during a period of initial tick control, we recommend a combined approach that includes environmental treatments.
The RMSF Rodeo was not designed to compare the efficacy of different tick control products. Seresto collars were selected because they provided a visible marker of dog treatment, were easy to apply, and represented the longest-acting product of this type with market approval. Similarly, the Bayer Advanced environmental acaricide was used because it was donated by the company, but also because it could be purchased and applied by homeowners without special licenses in the future. It is possible that similar tick control could also be achieved using different products; however, product longevity and effectiveness should be considered when selecting products.
This pilot project is subject to some limitations. Survey answers are subject to recall bias and interpretation, as well as perceived pressures to provide socially acceptable answers. Respondents in the RMSF Rodeo community may have felt a greater need to provide responses which inflate the project's success out of courtesy to the interviewer, which would bias our results away from the null. Neighborhoods were separated into intervention (RMSF Rodeo) and non-intervention (Non-Rodeo) communities; however, in some unusual cases we found RMSF Rodeo collars on dogs in Non-Rodeo communities, as a result of sharing of products between family members or translocation of dogs. While RMSF Rodeo and Non-Rodeo communities were geographically isolated from one another, unrestrained dogs may also have traveled outside of their intervention area or been translocated by human activity. These occurrences could result in spill-over between intervention and non-intervention communities, and may have introduced a bias towards the null hypothesis. Despite best efforts, dogs had the potential to be lost or duplicated among program records. Longitudinal analysis of all enrolled dogs was not possible as dogs were continually enrolled, died, or changed locations and identification tags were lost and duplicated; therefore, only cross-sectional data are reported. Our final limitation was the inability to track the Non-Rodeo areas for a second year to serve as a control group. Due to the overwhelming success of the RMSF Rodeo in 2012, the tribe implemented a modified tick control program in Non-Rodeo areas in 2013.
Reducing RMSF cases among tribal residents is the primary goal of the RMSF Rodeo. Control of tick activity in domestic and peridomestic locations is expected to reduce the risk of human exposure to
Since the development of this project, the need for
While the 2-year RMSF Rodeo program achieved a remarkable degree of tick control, it is worth noting that ticks were not completely eliminated in the RMSF Rodeo community. Tick control efforts will need to be maintained in coming years in order to keep the risk of tick bite and RMSF reduced in this community. It is unlikely that a full elimination scheme can be achieved for such a ubiquitous pest. However, it is the hope that adequate tick control in the environment and on animals will decrease the opportunities for human illness, and, when coupled with supportive care from well-trained physicians, cases can be caught sooner and deaths prevented.
We would like to thank the many organizations and charities that were involved in making this project possible. Substantial contributions of staff time and subject matter expertise were contributed from the Centers for Disease Control and Prevention, Indian Health Service, Arizona Department of Health Services and the United States Department of Agriculture. We would further like to thank Bayer for the donation of products, including the pre-market release of the Seresto collar. Lastly, we would like to thank Dr. Michael Levin, Elizabeth Studer and Lauren McColley for their contributions to the environmental tick collections and entomologic evaluations. Disclaimer: the findings and conclusions in this report are those of the authors and do not necessarily represent the official position of the Centers for Disease Control and Prevention and the Agency for Toxic Substances and Disease Registry. Reference to specific commercial products, manufacturers, companies, or trademarks do not constitute its endorsement or recommendation by the U.S. Government, HHS, or Centers for Disease Control and Prevention.