Next Article in Journal
Distribution of Insecticide Resistance Genetic Markers in the West Nile Virus Vector Culex pipiens from South-Eastern Romania
Previous Article in Journal
Characterizing Repellencies of Methyl Benzoate and Its Analogs against the Common Bed Bug, Cimex lectularius
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
Insects
Volume 13
Issue 11
10.3390/insects13111061
insects-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Laboratory Evaluation and Field Feasibility of Micro-Encapsulated Insecticide Effect on Rhodnius prolixus and Triatoma dimidiata Mortality in Rural Households in Boyacá, Colombia

by
Lídia Gual-Gonzalez
1,†,
Manuel Medina
2,†,
César Valverde-Castro
3,4,
Virgilio Beltrán
2,
Rodrigo Caro
2,
Omar Triana-Chávez
4,
Melissa S. Nolan
1 and
Omar Cantillo-Barraza
4,*
1
Arnold School of Public Health, University of South Carolina, Columbia, SC 29208, USA
2
Unidad de Control de Enfermedades Transmitidas por Vectores, Secretaría de Salud Boyacá, Tunja 150001, Colombia
3
Grupo de Investigación en Medicina Tropical, Universidad del Magdalena, Santa Marta 470003, Colombia
4
Grupo Biología y Control Enfermedades Infecciosas, Universidad Antioquia, Medellín 050010, Colombia
*
Author to whom correspondence should be addressed.
†
These authors contributed equally to this work.
Insects 2022, 13(11), 1061; https://doi.org/10.3390/insects13111061
Submission received: 13 October 2022 / Revised: 2 November 2022 / Accepted: 3 November 2022 / Published: 17 November 2022
(This article belongs to the Section Insect Pest and Vector Management)
Browse Figures
Review Reports Versions Notes

Abstract

:

Simple Summary

Vector control strategies need to adapt due to the increase in insecticide resistance among several vector species. Insecticide spraying requires great economic and logistical efforts due to repeated application every six months. This study evaluated the feasibility of micro-encapsulated insecticide on mortality on Rhodnius prolixus and Triatoma dimidiata and its effect on household colonization after one year application in a rural community in Colombia. Findings suggest the ability of this paint to prevent colonization and demonstrated positive population perception. Complementary use of insecticide spraying and micro-encapsulated paints suggest this could be a more efficient public health approach that could reduce costs and logistical efforts.

Abstract

Chagas disease is a neglected vector-borne zoonosis caused by the parasite Trypanosoma cruzi that is primarily transmitted by insects of the subfamily Triatominae. Although control efforts targeting domestic infestations of Rhodnius prolixus have been largely successful, with several regions in Boyacá department certified free of T. cruzi transmission by intradomicile R. prolixus, novel native species are emerging, increasing the risk of disease. Triatoma dimidiata is the second most important species in Colombia, and conventional control methods seem to be less effective. In this study we evaluated the efficacy and usefulness of micro-encapsulated insecticide paints in laboratory conditions and its applicability in rural communities to avoid triatomine domiciliation. Laboratory conditions measured mortality at 6 months and 12 months, with an average mortality between 93–100% for T. dimidiata and 100% for R. prolixus. Evaluation of triatomine infestation in rural households was measured after one year, with an overall perception of effectiveness in reducing household domiciliation. Although triatomines were still spotted inside and around the homes, our findings demonstrate the ability of micro-encapsulated insecticide to prevent colonization inside the households when comparing infestation rates from previous years. Current control measures suggest insecticide spraying every six months, which implies great economic cost and logistical effort. Complementary triatomine control measures with insecticide spraying and micro-encapsulated insecticide paint would make public health efforts more efficient and reduce the frequency of treatment.

1. Introduction

Chagas disease is a neglected vector-borne zoonosis caused by the parasite Trypanosoma cruzi primarily transmitted by hematophagous insects of the Triatominae subfamily established mostly in the Americas. Other transmission routes are less common, but include congenital transmission, blood transfusions, organ transplants, and oral transmission. It is estimated that more than 6 million people are living with infection and 70 million people live at risk of infection [1]. In Colombia, an estimated 1 to 2 million people are infected and 3.5 million people are at risk [2,3]. There, the burden of disease has an estimated cost of US $13 million due to healthcare expenses and productivity losses [4]. It mostly affects rural and poor communities with poor healthcare access and vector control infrastructure, challenging diagnostic and treatment opportunities [5]. Integrated vector control strategies are an effective measure to prevent Chagas disease, including chemical insecticide spraying in infested households, infrastructure improvement to reduce colonization, and educational campaigns to inform vulnerable communities on vector-borne infections [6,7].
Regional campaigns promoting Indoor Residual Spraying (IRS) have been carried out for the past 30 years in Latin America to eradicate the domestic infestation of triatomine species and eliminate exotic vector species. The Southern Cone Initiative (INCOSUR) in 1991 fostered the implementation of other regional initiatives [8]: the Andean Countries Initiative (ACI) [9] and the Initiatives for Chagas Disease Control in Central America and Mexico (IPCAM) [10] created in 1997 and 1998, respectively, followed by the Amazon Initiative in 2004 [11]. Elimination efforts have been largely successful, with 17 countries subsequently certified by the Pan-American Health Organization [12] to be free of vectorial transmission between 1999 and 2014 [13,14]. However, in the decade following these public health successes, other vector species have emerged and are becoming established. For example, Triatoma dimidiata and T. venosa have been recorded in areas where Rhodnius prolixus was eliminated [15,16], and T. brasiliensis, T. pseudomaculata, T. sordida and Panstrongylus megistus have been noted where Triatoma infestans was eliminated [17,18,19]. In a few instances, some of these secondary vectors of public health importance have recolonized and reinfested households after multiple treatments [17,18,19].
In Colombia, 26 triatomine species have been identified, highlighting the great species biodiversity nationally [20]. Overall, 66 municipalities in four departments, including Boyacá, were certified as “Domestic T. cruzi transmission by R. prolixus interrupted” in 2013, 2015, and 2019. This success was awarded due to the large-scale insecticide application in prioritized areas and reinfestation surveillance [13]. Insecticide spraying every six months has shown to be effective to maintain households free of R. prolixus; however, Triatoma dimidiata, the second most important vector in the region, has the ability to reinfest households previously treated, challenging the reduction of overall domestic triatomine presence [15]. Additionally, some vector-free certified municipalities have evidence of R. prolixus presence after insecticide application, implying there could be failure in elimination or possible insecticide resistance that needs further public health attention [21]. Boyacá, northeast of Bogotá-the capital district, is one of the most affected departments in Colombia. Intradomicile reinfestation has caused a reemergence of Chagas disease in the department. In Boyacá, 10 triatomine species have been identified, distributed across 63 municipalities; Triatoma dimidiata, Triatoma venosa, Panstrongylus geniculatus, and Rhodnius prolixus are the most commonly reported [22]. Triatomines persist in peridomestic and sylvatic environments, including in regions that have been certified free of vectorial transmission. Cumulatively, these emergent factors demand strategic intervention alternatives to combat ecological components maintaining these secondary and re-emerging vectors.
The primary chemicals recommended for triatomine control are λ-cyhalothrin, cypermethrin, and deltamethrin [23]. The use of these compounds as pesticides to control other agriculturally relevant pests–such as the palm weevil–have been suggested to overexpose palm-living triatomines to those insecticides, which are also recommended for Chagas vector control [24]. Limited evidence suggests long term exposure to these compounds can promote triatomine insecticide resistance, and it is becoming a concern for vector-control strategies [24]. Further, it has been hypothesized that these insecticide-resistant triatomines migrate to urbanized areas, surviving the control strategies used in traditional indoor spraying formulates [25]. Insecticide resistance is a growing concern in the region; however, most efforts are focused on Aedes aegypti mitigation [26,27,28]. New evidence suggests triatomine populations are also likely developing insecticide resistance, warranting novel interventions using alternative compounds for successful transmission interruption [29,30].
Insecticidal paint use is a well-known and community accepted alternative to indoor residual spraying [31,32,33]. Despite its historical use in Latin American countries, standardized protocols and rigorous studies evaluating optimal efficacy for triatomine reduction are lacking. As a strategy to prevent triatomine domiciliation, studies evaluating insecticidal paint have shown households stay free of triatomines for longer periods as compared to regular indoor domiciliary insecticide spraying, which could potentially be a successful alternative or a complementary intervention [34,35]. To understand the utility of this alternative strategy, we performed a mixed-methods study, evaluating the effect of insecticidal paint on Triatoma dimidiata and Rhodnius prolixus under laboratory conditions, and assessing the application of insecticidal paint in different households in the Boyacá department, Colombia.

2. Materials and Methods

2.1. Study Area

The study was conducted between July 2017 and December 2019, with laboratory experiments performed at the Universidad de Antioquia in Medellín and field intervention in Socotá municipalities (Boyacá department), Colombia. The Boyacá department is classified within the biogeographical zone of Sub-Tropical humid forest. The average temperature varies between 18–24 °C with an average annual precipitation between 1000–2000 mm. It is placed within the Andean mountain ranges and differences in altitudes provide a wide range of climates. Overall, 24 typical homes from the municipalities Chusvitá, Guaquira, La Vega, and Pueblo Nuevo were selected for the intervention study. Households were selected based on suitability to implement treatment, from areas with greater insect presence (Figure 1).

2.2. Insects

The study laboratory setting used established R. prolixus and T. dimidiata colonies from the Laboratory of Biology and Infectious Disease Control group (BCEI by its acronym in Spanish) at the Universidad de Antioquia, Medellín. Fourth and fifth instar R. prolixus nymphs were derived from the same colony and strain, original from a collection in Casanare department in 2010 prior to any insecticide application campaigns. Fourth and fifth instar T. dimidiata nymphs collected in a 2017 sampling event in Socotá municipality, Boyacá department, contributed to the established T. dimidiata colony. Both colonies have been kept in the BCEI laboratory without insecticide resistance pressure. All the insects used for the study had the same feeding time and were from the same hatch.

2.3. Insecticide Paint

Inesfly 5 A IGR paint (Inesfly Corporation, Valencia, Spain) is a water-based polymer coating with slow release microencapsulated insecticide. This commercially available paint is composed of a liposoluble micro-capsulated formulation containing organophosphate-based ingredients and chitin synthesis inhibitors: Diazinon 1.5%, Chlorpyrifos 1.5%, and Pyriproxyfen 0.063%. This domestic-friendly paint is widely available in Colombia and is used for insect control inside and outside the households.

2.4. Laboratory Bioassay

Bioassay prototype chambers were designed and built consisting of a brick base (10 cm × 20 cm × 20 cm) and four cardboard plates (20 cm × 40 cm) as lateral barriers and sealed with tape and silicone to avoid cracks where insects could escape (Figure 2). The internal walls were covered with Vaseline® (Unilever PLC, London, United Kingdom) to avoid the triatomines resting in the walls and to ensure contact with painted brick. A total of eight bricks were painted: six with Inesfly 5A IGR diluted in water, following manufacturer’s instructions, and two controls painted with a commercial paint without insecticide. The replicates made a total of eight sampling units to evaluate survival of 40 fourth and fifth instar R. prolixus nymphs and 40 fourth and fifth instar T. dimidiata nymphs. To evaluate residual effect of the paints, the insects were exposed for 60 min by placing them inside the chambers, and posteriorly removed. Mortality was evaluated at 24 h and 48 h post-exposure. The chambers were kept and used posteriorly at three different times repeating the same process to evaluate the long-term effect: T1 was the initial application, and insects were placed in each chamber 24 h after paint applications. T2 insects were placed at 3 months after paint applications, and T3 at 6 months. Evaluation of mortality was made through mechanical contact to assess stimulus response. For each repeat, 80 nymphs were used to evaluate the effectiveness of the paint using 10 insects of the same species in each chamber.

2.5. Field Application

Between November and December 2019, a mixed methods intervention study was performed to evaluate the effectivity of the paint to reduce the presence of triatomine insects. Inesfly 5 A IGR water-based paint product was applied to 24 selected households’ inside and outside walls. Paint was diluted 50% using distilled water for porous surfaces for a first layer and diluted 90% for a second application five hours later. Paint was applied using hand paint-rollers with ensured uniformity on the entirety of the surfaces. The households were monitored 12 months after paint application and homeowners were given a questionnaire. The questionnaire evaluated different risk factors such as house construction material, peridomicile characteristics and animal presence in the household, the presence of triatomines in the year following the insecticidal paint application, whether the individuals living in the household had experienced any adverse reactions, and demographic information. Field technicians performed a visual evaluation of the presence of triatomines revising the houses using the man/hour method, examining households for evidence of triatomine presence and triatomine eggs to determine household infestation, and/or colonization [36].

2.6. Ethics Statement

The study was conducted according to the guidelines of the Declaration of Helsinki and approved by the Ethics Committee for Animal Experimentation at the Universidad de Antioquia. Acta 112 de 14 de Agosto 2017.

3. Results

3.1. Laboratory Bioassay

As noted in Table 1-a, R. prolixus nymphs were susceptible for T1 at 24 h and 48 h; T2 at 24 h and 48 h; and T3 at 24 h and 48 h, with 100% mortality in all three experimental treatment groups. No mortality (0%) was ever noted in any control group. Treatment susceptibility was noted for the treated groups. The T. dimidiata group, however, showed slower mortality rate, as noted in Table 1-b. T. dimidiata nymphs demonstrated 80% susceptibility in one T1 replicate at 24 h (93.33% average for T1–24 h) and 90% susceptibility in one T2 replicate at 24 h (96.67% average for T2–24 h). All other experimental groups demonstrated susceptibility with 100% mortality.

3.2. Field Application

Results one year post application were collected through individual questionnaires to household members: responses were obtained for 21 of the 24 selected households. As noted in Table 2, household construction material was varied, with some being well-constructed (approximately half had brick and corrugated roof panels) and the other half had natural environmental housing material (e.g., mud, sticks, etc.). Domestic and agricultural animals were common in the peridomestic environment (91% of homes reported at least one animal). Almost all homes had ecological risk factors supportive of triatomine presence in the peridomestic environment (e.g., cracks in house walls, chicken coop, wood piles, trapiche mills, etc.). Lastly, sylvatic Trypanosoma cruzi-competent animal species were reported in most household surrounding areas: 95% of households reported opossum sightings; 62% reported rodents; and 24% reported bats. In summary, these homes represented epidemiologically high-risk scenarios for triatomine establishment.
Overall, 14 (66.7%) households responded having ever seen a triatomine, and the same proportion responded having seen a triatomine in the past year. From those that had seen a triatomine in the past year, 100% of them had seen them inside the household, in the peridomestic environment, and/or in the immediate sylvatic environment, without colonization. All respondents reported a reduction of triatomines in the year following insecticide application (100%), particularly around the household perimeter (95.2%). Triatomines inside the home were seen in: the entrance (85.7%), the bedroom (57.1%), the hallway (50.0%), the living room (14.3%), the kitchen (7.1%), the bathroom (7.1%) and the dining room (7.1%). In the peridomicile, triatomines originated from the chicken coop (92.9%), piles of rocks and/or wood (92.9%), stubble (71.4%), bird nests (35.7%), cactus (35.7%), and piles of bricks (21.4%). From the sylvatic environment, triatomines originated from: a crop field (57.1%) and nearby forest (42.9%). Lastly, allergic reactions were reported by 14.3% (3/21) of the respondents following insecticide paint application of their homes. Of these three homes with reported allergic reactions, two noted eye irritation and two noted dizziness after paint application. Additionally, field technicians did not observe any insects nor triatomine eggs presence that would bring evidence of household colonization.

4. Discussion

This is the first study evaluating insecticide paint effect in a laboratory and natural condition setting in Colombia. Results from this study indicated that insecticide paint Inesfly 5A IGR has a lasting effect on the mortality of R. prolixus and T. dimidiata, under laboratory conditions. These results are comparable to other evaluations in Triatoma infestans, strengthening the evidence of this product as a control measure [38,39]. T. dimidiata showed a reduced susceptibility to insecticide paint when measured at 24 h after contact, however, mortality was 100% at 48 h in all the evaluations, suggesting a great performance of the insecticidal paint. Indoor Residual Spraying (IRS) has been effective against R. prolixus, and T. dimidiata is now spreading in areas certified free of R. prolixus, which highlights the importance of control measures effective for T. dimidiata, an emerging species [15,40].
The reemergence of vectors in locations where the primary species was previously deemed eradicated raises concerns [15,16]. The current study undertook complementary controlled (laboratory-based) and real-world (field-based) investigations to ascertain the susceptibility of two prominent Colombian triatomine species to an innovative, commercially available insecticide. Our laboratory investigation revealed high susceptibility to Inesfly’s water-based insecticide indoor/outdoor paint. R. prolixus demonstrated high susceptibility at both 24 and 48 h, and T. dimidiata exhibited overall great susceptibility, with 100% mortality at 48 h. These findings were further substantiated in field trials. Field technicians did not observe any triatomines when attending houses, although homeowners reported triatomine sighting, and overall reduction was reported when comparing those results to previous investigations [21]. In summary, this proof-of-concept study confirms a positive impact of microencapsulated insecticidal paint among natural triatomine species that warrants continued surveillance to mitigate Chagas disease human transmission.
Our study is not the first one to investigate the application of insecticidal paints as an optional alternative to insecticide spray, with limited studies having displayed insecticide paint potential across the South American continent. Amelotti et al. evaluated insecticidal paint efficacy over a one-year period on Triatoma infestans populations in the Gran Chaco region of South America, and identified 81–100% susceptibility to painted surfaces using pyrethroid and organophosphate formulations [38]. Insecticidal paint evaluations in households of the Bolivian Chaco, using the same commercial paint, showed a demonstrable effect on mortality of T. infestans 34 months after application [34], and maintained infestation below 2% after 32 months [39]. The residual effect of the insecticidal paint has been reported to be longer than the residual effect of indoor spraying, suggesting this as an economic alternative for vector control. In the literature results on experimental settings that vary depending on the formulation of the paints, organophosphate formulated paints show greater mortality than pyrethroid formulation, supported by studies that show a better performance of organophosphate formulation over other insecticides [41]. The study from Maloney et al. found that the use of insecticidal paint composed by diazinon (1.5%), chlorpyrifos (1.5%), and pyriproxyfen (0.063%) produced significantly greater mortality than exposure to deltamethrin [31]. There is, however, an important controversy: the use of chlorpyrifos has been deemed successful in reducing pests and producing high insect mortality, however scrutinous investigations found associations with its use to neurological effects, endocrine disruption, and cardiovascular disease, which led to the ban of chlorpyrifos use in the United States and other countries [42]. Nevertheless, the method of delivery of chlorpyrifos through microencapsulated particles is designed to have significantly less toxicity in large vertebrates, and thus avoids harmful health outcomes [43]. Despite these published investigations, the overall literature is limited, and our current study fills this knowledge gap by adding pertinent contemporary results on the two leading vectors of public health importance in Colombia. Future investigations should consider evaluating further the safety of these microencapsulated paints on human health.
Triatoma dimidiata is an emerging secondary vector of public health importance. Like several other countries, the Boyacá department in Colombia has noted an increasing trend of this species in the peridomestic environment following PAHO’s 1990–2000’s R. prolixus elimination campaign. Historically, T. dimidiata has demonstrated a greater ability to shift between sylvatic and domestic environments compared to R. prolixus, and thus has an evidenced survival advantage. Moreover, a wide genetic variability could be beneficial for triatomines in areas such as Boyacá with diverse microclimates incorporating the insect’s most favorable conditions [44]. This versatility has allowed T. dimidiata to intrude and colonize households that eliminated R. prolixus modifying T. cruzi transmission risk distributions [21]. Insecticide spraying along with physical and chemical barriers has proved to reduce house infestation to a greater extent than spraying alone, suggesting increased efforts are needed to effectively control for T. dimidiata [45].
Today’s insecticidal paint manufacturers are able to create non-toxic continual-release formulas that allow for sustainable vector control in resource limited settings [43]. The average indoor residual spray lasts 6 months–in sharp contrast to our results, which demonstrate efficacy of the interventional insecticide paint up to 1-year post-application in a field study. Application of insecticidal paints on infested household walls has shown to be beneficial for the owners and evidence suggests strong community uptake [46]. Similar to a prior Honduran study [46], our results suggest great adherence, with a reported reduction of the presence of triatomines inside and along the household perimeter. A recent Peruvian community-based intervention using Datta and Mullainathan’s ‘behavioral design’ theory demonstrated that household-based vector control interventions, which empower the home owner, have long-last benefit for Chagas disease reduction [47]. Bolivian and Guatemalan eco-health interventions that educate and involve the community also found higher efficacy of national insecticide residual spraying programs [48,49]. Therefore, the current study’s high community participation is a notable finding in itself. Further, the fact that this insecticide can be used to treat other local agricultural pests (e.g., palm weevil) enhances the probability that this commercially available, low-cost solution will be used in between government vector control campaigns. Lastly, the novel combination of chemicals used for insecticidal paint can be a solution to single chemical resistance [24].
The results of this study showed the elimination of infestation and only sporadic appearances of insects around the households, as reported by homeowners. However, although insecticidal paint could be an alternative to insecticide spraying, other factors are involved in the effectiveness of maintaining triatomines averted from homes. Some conditions surrounding the households favor triatomine habitat, peridomestic animals keep triatomines fed around the houses, and piles of wood, rocks and other debris provide a place to hide for the insects [50]. Thus, vector control interventions should not be limited to only one type of intervention but allow for the use of effective traditional methods and novel alternatives to obtain more effective results. Additionally, vector control interventions should rely on complementary educational programs that allow for reduction of triatomine shelter in the household surroundings to decrease the risk of Chagas disease transmission.
A few investigation limitations are worth noting. The selection of homes for interventional paint application was restricted to households that had suitable conditions for paint treatment. Some of the households in the region are not adequate for water-based paints, nor have a surface suited for paint application, therefore the study findings and utility are limited to construction of wood, brick, and adobe. Moreover, a control group was unavailable, as for ethical reasons no households were left untreated, thus homes that did not receive the insecticide paint received indoor residual spray. These homes were not evaluated by survey due to logistical feasibility. However, the results from this proof-of-concept study suggest that paint application would reduce the triatomine presence and prevent triatomine dwelling inside the households. Additionally, our study evaluated for the first time the residual effect of the insecticidal paint on the two major species in the department of Boyacá, R. prolixus and T. dimidiata, increasing the external validity of the laboratory results. Lastly, additional species present in Boyacá department were not included which warrant future investigation: T. venosa, P. geniculatus, and P. rufotuberculatus.

5. Conclusions

In conclusion, this preliminary study demonstrates the efficacy and utility for insecticidal paint. Susceptibility to insecticidal was high, however insecticidal paint should be used in combination with other vector control techniques for greater efficacy. While insecticide spraying requires repeating the process every six months, insecticidal paint requires less frequency of application, with some reports showing more than 2 years of residual effect. Additionally, the low cost of this intervention would allow for greater uptake in the targeted population. This promising solution could maintain a reduced incidence of Chagas disease and continue the battle to eliminate vectorial transmission in Colombia.

Author Contributions

Conceptualization, O.C.-B. and M.M.; methodology, M.M., C.V.-C., V.B. and R.C.; formal analysis, L.G.-G. and M.M.; investigation, M.M., O.T.-C. and O.C.-B.; resources, O.T.-C. and O.C.-B.; data curation, L.G.-G.; writing—original draft preparation, L.G.-G., M.S.N. and O.C.-B.; writing—review and editing, L.G.-G., M.M., M.S.N. and O.C.-B.; funding acquisition, O.C.-B. All authors have read and agreed to the published version of the manuscript.

Funding

This study was carried out thanks to the agreement No. 001088 of 2016, 352 of 2018 and 3240 of 2020 signed between the Health Secretary of the Department of Boyacá, and the University of Antioquia (Biology and Control of Infectious Diseases Group, BCEI).

Institutional Review Board Statement

The study was conducted according to the guidelines of the Declaration of Helsinki and approved by the Ethics Committee for Animal Experimentation at the Universidad de Antioquia. Acta 112 de 14 de Agosto 2017.

Informed Consent Statement

Informed consent has been obtained from the resident.

Data Availability Statement

Data presented in this study are available upon request from the corresponding author.

Acknowledgments

We would like to thank the residents who agreed to participate in the field application study, and the technicians from the department of health that helped provide the surveys to the residents.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Echeverria, L.E.; Morillo, C.A. American Trypanosomiasis (Chagas Disease). Infect. Dis. Clin. N. Am. 2019, 33, 119–134. [Google Scholar] [CrossRef] [PubMed]
  2. Olivera, M.J.; Fory, J.A.; Porras, J.F.; Buitrago, G. Prevalence of Chagas disease in Colombia: A systematic review and meta-analysis. PLoS ONE 2019, 14, e0210156. [Google Scholar] [CrossRef] [PubMed]
  3. Moncayo, Á.; Silveira, A.C. 4—Current epidemiological trends of Chagas disease in Latin America and future challenges in epidemiology, surveillance, and health policy. Mem. Inst. Oswaldo Cruz. 2009, 104 (Suppl. 1), 17–30. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  4. Olivera, M.J.; Buitrago, G. Economic costs of Chagas disease in Colombia in 2017: A social perspective. Int. J. Infect. Dis. 2020, 91, 196–201. [Google Scholar] [CrossRef] [Green Version]
  5. Olivera, M.J.; Porras Villamil, J.F.; Toquica Gahona, C.C.; Rodríguez Hernández, J.M. Barriers to Diagnosis Access for Chagas Disease in Colombia. J. Parasitol. Res. 2018, 2018, 4940796. [Google Scholar] [CrossRef] [Green Version]
  6. Dias, J.C. Chagas’ disease and its control in Latin America: An analysis of possibilities. Cad Saude Publica 1993, 9, 201–209. [Google Scholar] [CrossRef] [Green Version]
  7. Yamagata, Y.; Nakagawa, J. Control of Chagas disease. Adv. Parasitol. 2006, 61, 129–165. [Google Scholar] [CrossRef]
  8. Organizacion Panamericana de la Salud. Iniciativa de Salud del Cono del Sur (INCOSUR): Comisión Intergubernamental del Cono Sur para la eliminacion del Triatoma infestants y la interrupcion de la Tripanosomiasis Américana Transfusional: Quinta Evaluación del Programa Nacional de Control de la Enfermedad de Chagas de Chile/Fifth Evaluation of National Program of Chagas Disease Control of Chile. In Proceedings of the Iniciativa de la Salud del Cono del Sur (INCOSUR), Santiago de Chile, Chile, 1–6 November 1999. [Google Scholar]
  9. Salvatella, R. Andean subregional Chagas disease area and the Andean initiative of Chagas disease. Mem. Inst. Oswaldo Cruz 2007, 102, 39–40. [Google Scholar] [CrossRef] [Green Version]
  10. Schofield, C.J.; Dujardin, J.P. Chagas disease vector control in Central America. Parasitol. Today 1997, 13, 141–144. [Google Scholar] [CrossRef]
  11. Aguilar, H.M.; Abad-Franch, F.; Dias, J.C.; Junqueira, A.C.; Coura, J.R. Chagas disease in the Amazon region. Mem. Inst. Oswaldo Cruz 2007, 102 (Suppl. 1), 47–56. [Google Scholar] [CrossRef]
  12. Pan American Health Organization (PAHO). Guidelines for the Diagnosis and Treatment of Chagas Disease; Pan American Health Organization: Washington, DC, USA, 2019; p. 176. [Google Scholar]
  13. Pan American Health Organization. Chagas Disease. Available online: https://www.paho.org/en/topics/chagas-disease (accessed on 12 July 2022).
  14. Hashimoto, K.; Schofield, C.J. Elimination of Rhodnius prolixus in Central America. Parasit. Vectors 2012, 5, 45. [Google Scholar] [CrossRef] [PubMed]
  15. Cantillo-Barraza, O.; Medina, M.; Zuluaga, S.; Valverde, C.; Motta, C.; Ladino, A.; Osorio, M.I.; Jaimes-Dueñez, J.; Triana-Chávez, O. Eco-epidemiological study reveals the importance of Triatoma dimidiata in the Trypanosoma cruzi transmission, in a municipality certified without transmission by Rhodnius prolixus in Colombia. Acta Trop. 2020, 209, 105550. [Google Scholar] [CrossRef] [PubMed]
  16. Medina, M.; Zuluaga, S.; Martínez, M.F.; Bermúdez, J.C.; Hernández, C.; Beltrán, V.; Velásquez-Ortiz, N.; Muñoz, M.; Ramírez, J.D.; Triana, O.; et al. Interrogating the transmission dynamics of Trypanosoma cruzi (Trypanosomatida, Trypanosomatidae) by Triatoma venosa (Hemiptera: Reduviidae) after the elimination of vector transmission by Rhodnius prolixus in Boyacá eastern Colombia. Front. Cell. Infect. Microbiol. 2022, 12, 998202. [Google Scholar] [CrossRef] [PubMed]
  17. Hashimoto, K.; Cordon-Rosales, C.; Trampe, R.; Kawabata, M. Impact of single and multiple residual sprayings of pyrethroid insecticides against Triatoma dimidiata (Reduviiade; Triatominae), the principal vector of Chagas disease in Jutiapa, Guatemala. Am. J. Trop. Med. Hyg. 2006, 75, 226–230. [Google Scholar] [CrossRef] [PubMed]
  18. Gómez-Palacio, A.; Triana, O. Molecular evidence of demographic expansion of the chagas disease vector Triatoma dimidiata (Hemiptera, Reduviidae, Triatominae) in Colombia. PLoS Negl. Trop. Dis. 2014, 8, e2734. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  19. Gurgel-Gonçalves, R.; Galvão, C.; Costa, J.; Peterson, A.T. Geographic distribution of chagas disease vectors in Brazil based on ecological niche modeling. J. Trop. Med. 2012, 2012, 705326. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  20. Guhl, F.; Aguilera, G.; Pinto, N.; Vergara, D. [Updated geographical distribution and ecoepidemiology of the triatomine fauna (Reduviidae: Triatominae) in Colombia]. Biomedica 2007, 27 (Suppl. 1), 143–162. [Google Scholar] [CrossRef] [Green Version]
  21. Velásquez-Ortiz, N.; Hernández, C.; Cantillo-Barraza, O.; Medina, M.; Medina-Alfonso, M.; Suescún-Carrero, S.; Muñoz, M.; Vega, L.; Castañeda, S.; Cruz-Saavedra, L. Estimating the genetic structure of Triatoma dimidiata (Hemiptera: Reduviidae) and the transmission dynamics of Trypanosoma cruzi in Boyacá, eastern Colombia. PLOS Negl. Trop. Dis. 2022, 16, e0010534. [Google Scholar] [CrossRef]
  22. Paez Restrepo, V.; Rubio Sandoval, C.; Ardila Roldan, S.C.; Tibaduiza Zacipa, T.E. Capítulo 4. Vigilancia De Triatominae (Hemiptera: Reduviidae) En Boyacá. In Vigilancia de Triatominae (Hemiptera: Reduviidae) en Colombia, 1st ed.; Parra-Henao, G.F.M., M. Angulo Silva, V., Eds.; Sic Editorial: Bucaramanga, Colombia, 2015; pp. 27–37. [Google Scholar]
  23. Pan American Health Organization. Métodos de Vigilancia Entomológica y Control de los Principales Vectores en las Américas; PAHO: Washington, DC, USA, 2021; p. 122. [Google Scholar]
  24. Calderón, J.M.; Fuya, P.; Santacoloma, L.; González, C. Deltamethrin resistance in Chagas disease vectors colonizing oil palm plantations: Implications for vector control strategies in a public health-agriculture interface. Parasites Vectors 2020, 13, 163. [Google Scholar] [CrossRef] [Green Version]
  25. Santo-Orihuela, P.L.; Vassena, C.V.; Carvajal, G.; Clark, E.; Menacho, S.; Bozo, R.; Gilman, R.H.; Bern, C.; Marcet, P.L. Toxicological, enzymatic, and molecular assessment of the insecticide susceptibility profile of Triatoma infestans (Hemiptera: Reduviidae, Triatominae) populations from rural communities of Santa Cruz, Bolivia. J. Med. Entomol. 2017, 54, 187–195. [Google Scholar] [CrossRef]
  26. Granada, Y.; Mejía-Jaramillo, A.M.; Zuluaga, S.; Triana-Chávez, O. Molecular surveillance of resistance to pyrethroids insecticides in Colombian Aedes aegypti populations. PLoS Negl. Trop. Dis. 2021, 15, e0010001. [Google Scholar] [CrossRef] [PubMed]
  27. Maia, P.C.R.; La Corte, R.; Pires, L.B.; Banfield, L.; Logan, J.G.; Lima-Camara, T.N. Increased Repellent Effect of DEET on Aedes aegypti (Diptera: Culicidae) Field Population. J. Med. Entomol. 2022, 59, 1368–1375. [Google Scholar] [CrossRef] [PubMed]
  28. Palomino, M.; Pinto, J.; Yañez, P.; Cornelio, A.; Dias, L.; Amorim, Q.; Martins, A.J.; Lenhart, A.; Lima, J.B.P. First national-scale evaluation of temephos resistance in Aedes aegypti in Peru. Parasit Vectors 2022, 15, 254. [Google Scholar] [CrossRef] [PubMed]
  29. Pessoa, G.C.; Vinãs, P.A.; Rosa, A.C.; Diotaiuti, L. History of insecticide resistance of Triatominae vectors. Rev. Soc. Bras. Med. Trop. 2015, 48, 380–389. [Google Scholar] [CrossRef] [Green Version]
  30. Mougabure-Cueto, G.; Picollo, M.I. Insecticide resistance in vector Chagas disease: Evolution, mechanisms and management. Acta Trop. 2015, 149, 70–85. [Google Scholar] [CrossRef] [PubMed]
  31. Maloney, K.M.; Ancca-Juarez, J.; Salazar, R.; Borrini-Mayori, K.; Niemierko, M.; Yukich, J.O.; Naquira, C.; Keating, J.A.; Levy, M.Z. Comparison of insecticidal paint and deltamethrin against Triatoma infestans (Hemiptera: Reduviidae) feeding and mortality in simulated natural conditions. J. Vector Ecol. 2013, 38, 6–11. [Google Scholar] [CrossRef] [Green Version]
  32. Llácer, E.; Dembilio, O.; Jacas, J.A. Evaluation of the efficacy of an insecticidal paint based on chlorpyrifos and pyriproxyfen in a microencapsulated formulation against Rhynchophorus ferrugineus (Coleoptera: Curculionidae). J. Econ. Entomol. 2010, 103, 402–408. [Google Scholar] [CrossRef]
  33. Mosqueira, B.; Chabi, J.; Chandre, F.; Akogbeto, M.; Hougard, J.M.; Carnevale, P.; Mas-Coma, S. Efficacy of an insecticide paint against malaria vectors and nuisance in West Africa—Part 2: Field evaluation. Malar. J 2010, 9, 341. [Google Scholar] [CrossRef] [Green Version]
  34. Alarico, A.G.; Romero, N.; Hernández, L.; Catalá, S.; Gorla, D. Residual effect of a micro-encapsulated formulation of organophosphates and piriproxifen on the mortality of deltamethrin resistant Triatoma infestans populations in rural houses of the Bolivian Chaco region. Mem. Inst. Oswaldo Cruz 2010, 105, 752–756. [Google Scholar] [CrossRef] [Green Version]
  35. Dias, J.C.P.; Jemmio, A. Sobre uma pintura inseticida para o controle de Triatoma infestans, na Bolívia. Rev. Soc. Bras. Med. Trop. 2008, 41, 79–81. [Google Scholar] [CrossRef]
  36. Chuit, R.; Paulone, I.; Wisnivesky-Colli, C.; Bo, R.; Perez, A.; Sosa-Stani, S.; Segura, E. Result of a first step toward community-based surveillance of transmission of Chagas’ disease with appropriate technology in rural areas. Am. J. Trop. Med. Hyg. 1992, 46, 444–450. [Google Scholar] [CrossRef] [PubMed]
  37. Peterson, D.; Barbeau, B.; McCaffrey, K.; Gruninger, R.; Eason, J.; Burnett, C.; Dunn, A.; Dimond, M.; Harbour, J.; Rossi, A.; et al. Human Rabies—Utah, 2018. MMWR Morb. Mortal. Wkly. Rep. 2020, 69, 121–124. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  38. Amelotti, I.; Catalá, S.S.; Gorla, D.E. Experimental evaluation of insecticidal paints against Triatoma infestans (Hemiptera: Reduviidae), under natural climatic conditions. Parasites Vectors 2009, 2, 30. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  39. Gorla, D.E.; Vargas Ortiz, R.; Catalá, S.S. Control of rural house infestation by Triatoma infestans in the Bolivian Chaco using a microencapsulated insecticide formulation. Parasites Vectors 2015, 8, 255. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  40. Parra-Henao, G.; Angulo, V.M.; Osorio, L.; Jaramillo-O, N. Geographic distribution and ecology of Triatoma dimidiata (Hemiptera: Reduviidae) in Colombia. J. Med. Entomol. 2016, 53, 122–129. [Google Scholar] [CrossRef]
  41. Schiøler, K.L.; Alifrangis, M.; Kitron, U.; Konradsen, F. Insecticidal paints: A realistic approach to vector control? PLoS Negl. Trop. Dis. 2016, 10, e0004518. [Google Scholar] [CrossRef] [Green Version]
  42. Hites, R.A. The Rise and Fall of Chlorpyrifos in the United States. Environ. Sci. Technol. 2021, 55, 1354–1358. [Google Scholar] [CrossRef]
  43. Simón-Moya, V.; Rodríguez-García, M. Introduction and Empirical Framework. In The Emergence of Social Entrepreneurship; Springer: Berlin/Heidelberg, Germany, 2021; pp. 135–143. [Google Scholar]
  44. Parra-Henao, G.; Quirós-Gómez, O.; Jaramillo-O, N.; Cardona, Á.S. Environmental determinants of the distribution of Chagas disease vector Triatoma dimidiata in Colombia. Am. J. Trop. Med. Hyg. 2016, 94, 767. [Google Scholar] [CrossRef] [Green Version]
  45. Ferral, J.; Chavez-Nuñez, L.; Euan-Garcia, M.; Ramirez-Sierra, M.J.; Najera-Vazquez, M.R.; Dumonteil, E. Comparative field trial of alternative vector control strategies for non-domiciliated Triatoma dimidiata. Am. J. Trop. Med. Hyg. 2010, 82, 60. [Google Scholar] [CrossRef]
  46. Avila Montes, G.A.; Ponce, C.; Ponce, E.; Martínez Hernández, M.; Flores, M. Insecticidal paint and fumigant canisters for Chagas’ disease control: Community acceptance in Honduras. Rev. Panam. Salud Publica 1999, 6, 311–320. [Google Scholar] [CrossRef]
  47. Buttenheim, A.M.; Levy, M.Z.; Castillo-Neyra, R.; McGuire, M.; Toledo Vizcarra, A.M.; Mollesaca Riveros, L.M.; Meza, J.; Borrini-Mayori, K.; Naquira, C.; Behrman, J.; et al. A behavioral design approach to improving a Chagas disease vector control campaign in Peru. BMC Public Health 2019, 19, 1272. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  48. Lardeux, F.; Depickère, S.; Aliaga, C.; Chavez, T.; Zambrana, L. Experimental control of Triatoma infestans in poor rural villages of Bolivia through community participation. Trans. R. Soc. Trop. Med. Hyg. 2015, 109, 150–158. [Google Scholar] [CrossRef] [PubMed]
  49. Castro-Arroyave, D.; Monroy, M.C.; Irurita, M.I. Integrated vector control of Chagas disease in Guatemala: A case of social innovation in health. Infect. Dis. Poverty 2020, 9, 25. [Google Scholar] [CrossRef] [PubMed]
  50. Sarquis, O.; Sposina, R.; de Oliveira, T.G.; Mac Cord, J.R.; Cabello, P.H.; Borges-Pereira, J.; Lima, M.M. Aspects of peridomiciliary ecotopes in rural areas of northeastern Brazil associated to triatomine (Hemiptera, Reduviidae) infestation, vectors of chagas disease. Mem. Inst. Oswaldo Cruz 2006, 101, 143–147. [Google Scholar] [CrossRef] [PubMed]
Insects 13 01061 g001 550
Figure 1. (A). Examples of selected households based on suitability before applying the paint (1) and after applying the paint (2). (B). Map of the selected municipalities from the Socatá region, Boyacá department, Colombia.
Figure 1. (A). Examples of selected households based on suitability before applying the paint (1) and after applying the paint (2). (B). Map of the selected municipalities from the Socatá region, Boyacá department, Colombia.
Insects 13 01061 g001
Insects 13 01061 g002 550
Figure 2. Bioassay prototype chambers for triatomine exposure to micro-encapsulated insecticidal paint. Triatomines were exposed for 1 h inside the chambers for follow-up at 24–48 h post exposure.
Figure 2. Bioassay prototype chambers for triatomine exposure to micro-encapsulated insecticidal paint. Triatomines were exposed for 1 h inside the chambers for follow-up at 24–48 h post exposure.
Insects 13 01061 g002
Table
Table 1. Mortality% to treated and control chamber prototypes in R. prolixus and T. dimidiata for each application time.
Table 1. Mortality% to treated and control chamber prototypes in R. prolixus and T. dimidiata for each application time.
a. Rhodnius prolixus
T1T2T3
n24 h 148 h24 h 148 h24 h 148 h
Control10000000
Replica 110100100100100100100
Replica 210100100100100100100
Replica 310100100100100100100
b. Triatoma dimidiata
T1T2T3
n24 h 148 h24 h 148 h24 h 148 h
Control10000000
Replica 1108010090100100100
Replica 210100100100100100100
Replica 310100100100100100100
1 The first evaluation showed some insects had died and some were in a “knock-out” state–not moving, or having difficulty walking or moving antennae–after a stimulus response. All knock out insects were dead in the 48 h evaluation.
Table
Table 2. Description of household characteristics.
Table 2. Description of household characteristics.
DescriptionN * (%)
Wall materialsAdobe11(52.4)
Brick10 (47.6)
Wood2 (9.5)
Mud and Bahareque1 (4.8)
Roof materialsZinc10 (47.6)
Mud16 (76.2)
Asbestos cement6 (28.6)
Floor materialsGround/soil10 (47.6)
Cement19 (90.5)
Tiles4 (19.1)
Wood1 (4.8)
Features surrounding the householdChicken Coop19 (90.5)
Barn3 (14.3)
Pigsty6 (28.6)
Oven10 (47.6)
Mill6 (28.6)
Wood pile20 (95.2)
Rock pile19 (90.5)
OtherAny sight of wall cracks15 (71.4)
Average number of bulbs inside the home [Mean ± SD [37]]3.76 ± 1.48
Average number of bulbs outside the home [Mean ± SD]1.14 ± 0.91
Domestic animal presenceHomes with animals20 (95.2)
Dogs19 (90.5)
Chickens19 (90.5)
Pigs8 (38.1)
Cows15 (71.4)
Horses9 (42.9)
Cats17 (81.0)
Domestic birds8 (38.1)
Domestic rabbits1 (4.8)
Have seen wild animal in the surroundingsOpossum20 (95.2)
Rodent13 (61.9)
Bat5 (23.8)
Pigeon8 (38.1)
Rabbit2 (9.5)
* Percentages may add up to more than 100% due to respondent’s multiple answer option.
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Gual-Gonzalez, L.; Medina, M.; Valverde-Castro, C.; Beltrán, V.; Caro, R.; Triana-Chávez, O.; Nolan, M.S.; Cantillo-Barraza, O. Laboratory Evaluation and Field Feasibility of Micro-Encapsulated Insecticide Effect on Rhodnius prolixus and Triatoma dimidiata Mortality in Rural Households in Boyacá, Colombia. Insects 2022, 13, 1061. https://doi.org/10.3390/insects13111061

AMA Style

Gual-Gonzalez L, Medina M, Valverde-Castro C, Beltrán V, Caro R, Triana-Chávez O, Nolan MS, Cantillo-Barraza O. Laboratory Evaluation and Field Feasibility of Micro-Encapsulated Insecticide Effect on Rhodnius prolixus and Triatoma dimidiata Mortality in Rural Households in Boyacá, Colombia. Insects. 2022; 13(11):1061. https://doi.org/10.3390/insects13111061

Chicago/Turabian Style

Gual-Gonzalez, Lídia, Manuel Medina, César Valverde-Castro, Virgilio Beltrán, Rodrigo Caro, Omar Triana-Chávez, Melissa S. Nolan, and Omar Cantillo-Barraza. 2022. "Laboratory Evaluation and Field Feasibility of Micro-Encapsulated Insecticide Effect on Rhodnius prolixus and Triatoma dimidiata Mortality in Rural Households in Boyacá, Colombia" Insects 13, no. 11: 1061. https://doi.org/10.3390/insects13111061

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop