Next Article in Journal
Periodic Physical Disturbance: An Alternative Method for Controlling Sitophilus zeamais (Maize Weevil) Infestation
Next Article in Special Issue
Looking Backward, Looking Forward: The Long, Torturous Struggle with Mosquitoes
Previous Article in Journal
Prey-Mediated Effects of Drought on the Consumption Rates of Coccinellid Predators of Elatobium abietinum
Previous Article in Special Issue
Comparison of Model Predictions and Laboratory Observations of Transgene Frequencies in Continuously-Breeding Mosquito Populations
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

Research Contributing to Improvements in Controlling Florida’s Mosquitoes and Mosquito-borne Diseases

by
Walter J. Tabachnick
1
1
Florida Medical Entomology Laboratory, University of Florida, IFAS, 200 9th St. SE, Vero Beach, FL 32962, USA
1
Indian River Mosquito Control District, Vero Beach, Florida, USA
1
Manatee County Mosquito Control District, Palmetto, Florida, USA
Insects 2016, 7(4), 50; https://doi.org/10.3390/insects7040050
Submission received: 18 August 2016 / Revised: 21 September 2016 / Accepted: 23 September 2016 / Published: 28 September 2016

Abstract

:
Research on mosquitoes and mosquito-borne diseases has contributed to improvements in providing effective, efficient, and environmentally proper mosquito control. Florida has benefitted from several research accomplishments that have increased the state’s mosquito control capabilities. Research with Florida’s mosquitoes has resulted in the development of ecologically sound management of mosquito impoundments on Florida’s east coast. This strategy, called Rotational Impoundment Management (RIM), has improved the ability to target the delivery of pesticides and has helped to reduce non-target effects and environmental damage. Research has led to the development of an arbovirus surveillance system which includes sentinel chicken surveillance, real time use of environmental contributing factors like meteorology and hydrology to target mosquito control, as well as public health efforts to mitigate disease outbreaks to areas with risk of disease. These research driven improvements have provided substantial benefits to all of Florida. More research is needed to meet the future challenges to reduce emerging pathogens like Zika virus and the consequences of environmental changes like global climate change that are likely to influence the effects of mosquito-borne pathogens on human health and well-being.

1. Introduction

Research on mosquitoes and humankind’s war against mosquito pests and mosquito vectors entered the modern era at the beginning of the 20th century with the U.S. Yellow Fever Commission’s demonstration that Aedes aegypti transmitted the dreaded yellow fever virus (YFV) [1]. This subsequently led to the first triumphs against mosquito-borne disease through effective mosquito control spearheaded by William Gorgas who directed the successful control of Ae. aegypti in Havana Cuba in 1900, and then again in the Panama Canal construction project completed in 1914. As a result, yellow fever was virtually eliminated from Havana in 1902 for the first time in approximately 300 years, and later essentially eliminated in the Panama Canal Zone, which contributed greatly to the successful completion of the canal by the U.S. Previously, France had failed in its attempt to build a canal across the Isthmus of Panama nearly 25 years before in part due to malaria and yellow fever epidemics. Since that time much knowledge has been accumulated about mosquito biology for many of the approximately 3500 described species of mosquitoes throughout the world, with greatest attention to the species of mosquitoes that are the major human pests and those that transmit a variety of pathogens affecting human and non-human hosts. General information on mosquito biology and mosquito control can be found elsewhere [2,3,4].
Knowledge of mosquitoes has been vital to humankind’s ability to control mosquitoes and mosquito-borne diseases. The myriad of ways such knowledge has improved mosquito control are beyond the scope of this review. An introduction to the vast biological literature is available elsewhere in selected reviews describing the influence on mosquito control of systematics [5], population genetics [6], genetics [7], behavior [8], physiology, and ecology [9]. Research in California and collaborations with California mosquito control programs reviewed elsewhere [10] continue to improve mosquito control [11].
Here I outline the impact of research on mosquito control methods by discussing studies in Florida and the improvements these efforts have had on mosquito control. Florida’s habitats and the resulting large mosquito populations were the reasons for organizing Florida’s first mosquito control district nearly 100 years ago. There are now mosquito control organizations in many parts of the state to fight what are considered nuisance or pest mosquitoes, and to also combat Florida’s species of mosquitoes that transmit mosquito-borne pathogens [12,13]. The mission of Florida’s mosquito control organizations is to protect residents and visitors from mosquitoes using effective, efficient, and environmentally proper mosquito control [14].
Florida’s mosquito control professionals, represented by the Florida Mosquito Control Association, believe that information about mosquito biology is essential to accomplish its mission to protect the public from mosquitoes [14]. Studies in Florida have provided information about disease surveillance, mosquito biology, wetlands ecology, human-made mosquito problems, disease prevention, repellents and attractants, improving existing pesticide application technology, resistance to insecticides, non-target organisms, and biocontrol [15]. One study on sampling mosquitoes and the factors influencing mosquito flight patterns illustrates the long history of Florida’s research on mosquitoes and mosquito control [16].The commitment to obtain knowledge about mosquito biology in Florida led to the development of a Florida state-supported mosquito biology research program to improve mosquito control more than 60 years ago under the leadership of John H. Mulrennan Sr. and Dr. Maurice Provost, both then with the Bureau of Entomology of the Florida State Board of Health [13]. Their leadership resulted in the creation of the Florida Entomological Research Center that later became the University of Florida’s Florida Medical Entomology Laboratory (FMEL) in Vero Beach. This later led to the John Mulrennan Public Health and Entomology Research and Education Center (PHEREC) when several of the Vero Beach faculty were relocated to Panama City. PHEREC later became part of Florida A & M University until it was closed in 2011. Much of the information on the biology of Florida’s mosquitoes and the use of this information to improve mosquito control were due to the efforts of the faculty and staff at these two laboratories working in collaboration with many of Florida’s mosquito control and public health professionals. Table 1 shows the extent of some of the contributions of these two laboratories since 1960 to several selected subjects about the biology of Florida’s mosquitoes and several of the pathogens they transmit. From 30%–60% of all peer reviewed articles involving Florida mosquito ecology, Florida Aedes aegypti, Florida mosquito control, Florida St. Louis encephalitis, and Florida West Nile virus were produced by these laboratories. The efforts of the laboratories have been supported over the years by the Florida Mosquito Control Research Program (FMCRP). This program is administered by the Florida Department of Agriculture and Consumer Services (FDACS) that is legislatively authorized to use not more than 20% (Florida Statute 388.261) of Florida’s funds from taxes generated by the Florida waste tire tax to support the research program (Florida Statute 403.709). Florida mosquito control efforts have also benefitted from research conducted by the U. S. Department of Agriculture (USDA), Agricultural Research Service, Center for Medical, Agricultural and Veterinary Entomology (CMAVE), located in Gainesville, Florida. Though CMAVE’s mission addresses national issues, CMAVE scientists have provided a substantial amount of information on trapping, surveillance, and biocontrol that has also been valuable to Florida mosquito control [15].
The goals of this manuscript are to: (1) review three research areas resulting from programs supported in part by the FMCRP, and/or provided by FMEL or PHEREC, and/or conducted by Florida’s mosquito control organizations: Rotational Impoundment Management (RIM), mosquito spray technologies and non-target effects of mosquito control, and arbovirus surveillance; (2) provide information on some of the impacts of these accomplishments in improving mosquito and mosquito-borne disease control; (3) present examples of current challenges requiring research on the biology of mosquitoes.

2. The Florida Mosquito Control Research Program (FMCRP)

The FMCRP has provided state funds for research to improve mosquito control and the ability to effectively combat mosquito-borne diseases throughout Florida for nearly 30 years [17]. The program is managed by FDACS currently with an annual budget of $500,000. These funds support projects that are important to the entire state. For example, information was provided through the FMCRP on the biology of the primary mosquito vectors of West Nile virus (WNV), St. Louis encephalitis virus (SLEV), and eastern equine encephalitis virus (EEEV) in Florida. This information is the basis of Florida’s ability to reduce populations of the dangerous vector mosquitoes reviewed below. Information provided by FMCRP supported projects on new insecticides, novel strategies to mitigate mosquito populations while reducing the impact of mosquito control practices on the environment, and on non-target organisms and new biocontrol methods. The FMCRP provided the information that is the basis of Florida’s sentinel chicken surveillance system to assess transmission of several arboviruses and serve as an early warning system for epidemics. This system has been Florida’s first line of defense against mosquito-borne disease like West Nile fever, and St. Louis and eastern equine encephalitides. The Florida Coordinating Council on Mosquito Control (FCCMC) consists of representatives of several Florida state agencies including Florida’s Department of Agriculture and Consumer Services (FDACS), Department of Health, Department of Environmental Protection, Fish and Wildlife, several environmental groups, USDA, Florida Mosquito Control, and Florida’s state research universities. Each year the FCCMC recommends the high priority needs for information to improve mosquito control to FDACS. The established priorities are then used by an independent research selection committee of scientific experts administered by FDACS. This committee evaluates the quality of submitted projects to ensure that selected projects provide important, high priority information while also being scientifically sound.
The FMCRP goal is to provide information that will directly benefit Florida mosquito and mosquito-borne disease control. The focus of this paper is on research studies in Florida, in large part supported by the FMCRP, to the exclusion of many important research studies elsewhere that have also benefitted mosquito control. The references provided here will lead readers to the extensive literature describing other contributions. The following are a few selected accomplishments that illustrate the impact of Florida’s research programs on the biology of mosquitoes and on methods to control them.

3. Improved Mosquito Impoundments Using Rotational Impoundment Management (RIM)

Many methods are available to help control mosquito production from wetlands [18]. For example, along Florida’s east coast many salt marsh or mangrove forest areas produce huge populations of Aedes taeniorhynchus and Aedes sollicitans that are effectively controlled using impoundments. These species of mosquitoes do not lay their eggs on standing water but prefer moist marsh soils [19]. Dikes are used to separate the impounded area from nearby waterways on Florida’s east coast in the Indian River Lagoon that are utilized to control the water levels in the impounded areas for mosquito control. Flooding the impounded areas at times of the year when saltmarsh mosquitoes are seeking moist substrate to lay eggs prevents oviposition and results in fewer mosquitoes in the next generation. Research demonstrated that impounded wetlands had many detrimental effects on the wetlands ecology [20]. The impoundments degraded wetlands, they allowed nonnative plants to invade, and they interfered with the migration and reproduction of fish and other organisms that also used the wetland habitat (Figure 1a).
Decades of research has shown that mosquito production can be halted by reconnecting impoundments to the lagoon via culverts and flooding the impoundments only during the summer mosquito re-producing season (September through May) [21,22,23]. Opening the culverts allow fishes, shrimps, and crabs to regain access to the wetland. Wetland vegetation is also restored (Figure 1b). This mosquito control method is known as RIM [20,22,24].
The benefits of the research on impoundments and RIM have been substantial. There have been significant savings to east Florida mosquito control in not having to apply costly larvicides because of RIM. RIM has extended the usefulness of mosquito impoundments to control both saltmarsh mosquitoes and improve natural resources. The savings in using RIM rather than spraying the estimated 40,000 impounded acres of marsh on the east coast of Florida is roughly $10,000,000 annually (40,000 × $25/acre for Bti × 10 treatments annually) [25]. RIM has returned 40,000 acres in east Florida to productive marsh acreage, maintaining their economic value to the area that has been estimated at $10,000/acre annually. This represents an economic benefit of approximately $400,000,000 annually.

4. Improved Pesticide Application

Adulticides and larvicides, delivered aerially or by ground vehicles, are important tools for mosquito control. Ultra-low volume (ULV) sprays have been the preferred method for delivery of mosquito control adulticides for nearly 60 years (Figure 2). ULV is the minimum effective volume of the product without any further dilution [26]. The history and development of ULV applications for mosquito adulticides are reviewed in more detail elsewhere [27,28,29].
Research has greatly improved the effectiveness, efficiency, and environmental propriety of adulticiding for mosquito control [26,29,30]. Studies provided information on the importance of the adulticide droplet size on the effectiveness of aerial ULV [27,31,32], the calibration of spray, dosage rates and effects of different spray systems on droplet size spectrums [33,34,35,36,37], the importance of meteorological effects on adulticide applications [27,35,38,39,40,41], barriers to adulticide effectiveness [26,42,43,44], improvements to measure pesticide residues to reduce non-target effects [45], and tests to gauge the non-target effects of mosquito control ULV pesticides [46,47,48,49,50].
The benefits of research on ULV applications has provided Florida mosquito control organizations with greater precision and accuracy for adulticide applications. Latham [51] advised that the ideal aerosol for mosquito control would: (1) have a high ability to impact a mosquito; (2) remain airborne for long periods, thus increasing the probability of contacting a mosquito; (3) not contain more than a single toxic dose in a droplet to avoid wasting pesticide. The studies above showed that adulticides are most effective when meteorological conditions are favorable to enable the spray cloud to drift to the target area, avoid barriers such as vegetation and canopy, and avoid high deposition levels with effects on non-target species. Figure 3 provides some of the criteria used to ensure a successful adulticiding mission. The savings to mosquito control is due to having greater ability for adulticiding to impact mosquitoes. There is more precision to impact specific target areas with a dose that is the minimal dose of pesticide capable of effectively killing the mosquito, with spray that does not have local high deposition in an area, and therefore with minimal non-target effects of the adulticide. Targeting adulticide missions to impact areas with large numbers of mosquitoes reduces the need for more widespread adulticiding [52].
The savings due to improved adulticiding methods that have increased mosquito control efficiency, effectiveness, and environmental propriety vary depending on variations between mosquito control organizations in their reliance on mosquito adulticides. Manatee County Mosquito Control District (MCMCD) illustrates the potential impact of improved ULV adulticiding methods [52]. MCMCD estimates that converting adulticide sprays to more effective droplet sizes, approximately 10–30 microns in diameter, provides a significant improvement for reducing mosquito populations while using similar or lower application rates. Prior to changing droplet spectrums MCMCD applied the adulticide Dibrom at 0.67–0.75 oz./acre while current applications use 0.5–0.6 oz/acre or 20%–25% less material to treat the same area [52]. MCMCD treats on average approximately 750,000 acres annually with Dibrom currently at a cost of approximately $200 per gallon, resulting in a savings of approximately $190,000 a year due to using the smaller droplet size. In addition, MCMCD uses improved targeted delivery of adulticides that includes GPS and meteorology that takes advantage of wind effects for spray drift to minimize high adulticide deposits that might impact non-target organisms on the ground or in nearby waters [51]. MCMCD currently applies aerial adulticide sprays only at sunset and later to minimize impacts on day-active honeybees. Research on the impact of adulticides on honeybees showed that the newer spray systems that produced the smaller droplet sizes were far less damaging on bees clustered outside the hive and had no impact on overall honey yield [48]. This is a substantial improvement when compared to the previously used larger droplet sprays where higher mortality was seen in bees clustered on the outside of hives and honey yield was believed to have been impacted.

5. Florida Arbovirus Surveillance, Predicting Epidemics, and Mosquito Control

Studies in Florida have focused on the Culex-borne arboviruses beginning with studies on the mosquito vectors responsible for the SLEV Tampa epidemic in 1962 [53]. Ensuing outbreaks of SLEV like the 1990 south Florida epidemic, and in recent years the transmission of WNV in Florida by the same Culex vectors of SLEV, focused research on the conditions in Florida that increase risk for arbovirus transmission. This research has improved Florida’s capability to predict arbovirus transmission by Culex in Florida and is reviewed elsewhere [54,55].
Florida mosquito control and public health professionals use an arbovirus surveillance program built upon research to assess the risk for an arbovirus epidemic of the Culex-borne arboviruses, especially SLEV, WNV, and EEEV [56,57]. The goal is to use surveillance to take actions to prevent or mitigate an epidemic through targeted mosquito control to high-risk areas and to provide warnings to individuals in those areas to take precautions to reduce human infections.
Florida’s arbovirus surveillance for Culex-borne arboviruses is based on the knowledge that Florida’s mosquito vectors of these arboviruses, particularly Culex nigripalpus and Culex pipiens quinquefasciatus, primarily feed on avian hosts, have populations that are influenced by rainfall, and that substantial transmission is more likely with populations of mosquitoes with older female mosquitoes with a higher probability of having more than one or two gonotrophic cycles. Florida’s climate—which features a wide range of weather conditions, including winter freezes—also influences the risk for subsequent transmission by species of Culex [58,59]. Research on Culex vectors led to the establishment of Florida’s sentinel chicken surveillance program with hundreds of sentinel chicken flocks located throughout much of Florida. The chickens in these flocks are bled periodically (twice weekly in many districts) by mosquito control or public health professionals and sent to a testing laboratory of the Florida Department of Health to detect antibodies to EEEV, SLEV, and WNV. The results are then used to gauge the transmission in the area of the flock. Culex nigripalpus females have blood feeding behaviors and oviposition that are synchronized with rainfall and the flooding of temporary oviposition sites [60]. Culex nigripalpus and Cx. p. quinquefasciatus females retain their eggs until rainfall increases available oviposition sites. As a result, these females that have been infected on the first blood meal may actually complete the intrinsic incubation period during a drought, and be ready to transmit even after the first gonotrophic cycle [61]. The reliance on rainfall for large mosquito populations has led to using hydrologic conditions to predict Culex-arbovirus transmission in Florida [62]. The hydrological conditions in Florida shown as average depth of groundwater for a one week period (Figure 4a) and the resulting risk for WNV transmission [54] (Figure 4b) illustrate the information used to assess risk in south Florida.
Research has shown that rainfall events in Florida have a specific signature for the timing of rainfall and drought conditions that coincide with avian breeding cycles resulting in more mosquito-avian transmission that then increases the risk for concomitant human infections [62]. Specifically, spring rain events produce Culex populations that if followed by a period of drought will force mosquitoes and birds together around the remaining water sources. This serves to increase virus prevalence in both hosts (avians) and vectors (mosquitoes). After the drought period ends with subsequent rainfall, the Culex females move to the new water sources thereby increasing contact with other hosts like humans with subsequent transmission to humans. Figure 5 shows the signature for rainfall and drought events in Florida that predict Culex-borne epidemics of SLEV and WNV.
The age structure of Cx. nigripalpus or Cx. p. quinquefasciatus populations is another important factor in assessing risk. Samples of Cx. nigripalpus or Cx. p. quinquefasciatus females in a population can be assessed for parity, blood feeding status, and age using morphological changes in ovarian and tracheole structure that occur during egg maturation and oviposition. This can be used to establish the number of gonotrophic cycles in these females [63,64] to provide additional information about the risk for arbovirus transmission in an area. Populations containing a large percentage of old female mosquitoes, such as females that have passed through several gonotrophic cycles, increase the risk for transmission if virus is present in the area.
Florida’s arbovirus risk prediction surveillance system for Culex-borne arboviruses has provided information of possible high-risk areas where mosquito control and public health action is required. Equally important, the surveillance information has also been used in deciding there was little transmission risk in the face of an isolated transmission event to a human or animal. Hence efforts to mitigate transmission can be targeted to areas where there are several types of information indicating the risk for substantial transmission. This provides greater accuracy enabling mosquito control to be more efficient, effective, and environmentally proper. The 2005 West Nile epidemic in Pinellas County illustrates the benefit of Florida’s surveillance programs. In 2005, Pinellas County Mosquito Control District (PCMCD) effectively applied adulticides and control efforts in the area of the county circumscribed by three sentinel chicken flocks that had significantly higher WNV transmission compared to their other sentinel flocks. This was in advance of the first WNV human cases in this area. There were eventually 18 human WNV cases in 2005 in Pinellas County. Estimates of potential cases based on the transmission rate to Pinellas County sentinel chickens was 2–20 cases per week. Transmission never expanded outside the identified transmission zone, and transmission ended in early August 2005 well before the usual end of the mosquito season in this area [55]. Surveillance and aggressive vector control helped to reduce the magnitude of the epidemic. The savings were apparent in confining adulticiding and other efforts to the high-risk zone without county-wide spraying. Efficient, effective, and environmentally proper mosquito control was employed.

6. Challenges and Conclusions

The benefits from research on mosquito control are many. The accomplishments reviewed above are selected examples. Mosquito control and mosquito-borne disease control will continue to improve with more research. Research is needed to improve RIM, pesticide delivery systems, and arbovirus surveillance in general. New tools are needed to improve mosquito and mosquito-borne disease control. This means new pesticides, new effective biological control strategies, including the novel use of genetically modified organisms, which must be shown to be environmentally safe. Omitted from this review are the challenges in combatting other arboviruses, better prediction for high-risk areas for epidemics, emerging arboviruses, the impact of environmental factors like global climate change, and the establishment of arboviruses in new areas and environments. The challenges to obtaining the required information are reviewed elsewhere [65,66,67,68,69].
Mosquito control throughout the world faces great challenges [70]. For example, the ability of Florida and the U.S. to be effective against Aedes-borne arboviruses like dengue virus (DENV), chikungunya virus (CHIKV), yellow fever virus (YFV), and Zika virus (ZIKV) presents new challenges. These arboviruses and their Aedes vectors provide different vector-virus systems compared to Florida’s experience with the Culex-arbovirus systems like SLEV and WNV. There is a substantial amount of information concerning mosquito control efforts against Ae. aegypti in particular that shows the difficulties in providing mosquito control against this species [71,72,73,74,75]. Currently U.S. mosquito control generally does not have much experience with an Ae. aegypti-borne virus epidemic. It will be vital for the U.S. to provide sufficient support for research on various arbovirus systems with the goal to improve control capabilities to meet these new challenges and also to meet the challenges for yet unidentified, newly evolving arbovirus threats to human health and well-being.

Acknowledgments

I appreciated the thoughtful comments and assistance of E. John Beidler, Nathan Burkett-Cadena, Douglas B. Carlson, G. Alan Curtis, and Donald Shroyer who shared their ideas that greatly improved this manuscript. I thank three anonymous reviewers for their suggestions. Mark D. Latham provided information about the benefits of improvements in mosquito adulticiding technology to Manatee County Mosquito Control District. James Newman’s assistance with the figures is greatly appreciated.

Conflicts of Interest

The author declares no conflict of interest.

References

  1. Crosby, M.C. The American Plague: The Untold Story of Yellow Fever, the Epidemic that Shaped Our History; Penguin Group: New York, NY, USA, 2006. [Google Scholar]
  2. Becker, N.; Petri, D.; Boase, C.; Lane, J.; Zgomba, M.; Dahl, C.; Kaiser, A. Mosquitoes and Their Control; Kluwer Academic/Plenum Publishers: New York, NY, USA, 2003. [Google Scholar]
  3. Marquardt, W.H. Biology of Disease Vectors, 2nd ed.; Elsevier Academic Press: Amsterdam, The Netherlands, 2004. [Google Scholar]
  4. Eldridge, B.F.; Edman, J. Medical Entomology: A Textbook on Public Health and Veterinary Problems Caused by Arthropods; Kluwer Academic Publisher: Dordrecht, The Netherlands, 2012. [Google Scholar]
  5. Zarowiecki, M; Loaiza, J.R.; Conn, J.E. Towards a new role for vector systematics in parasite control. Parasitology 2011, 138, 1723–1729. [Google Scholar] [CrossRef] [PubMed]
  6. Tabachnick, W.J.; Black, W.C. Making a case for molecular population genetic studies of arthropod vectors. Parasitol. Today. 1995, 11, 27–30. [Google Scholar] [CrossRef]
  7. Wang, S.; Jacobs-Lorena, M. Genetic approaches to interfere with malaria transmission by vector mosquitoes. Trends Biotech. 2013, 31, 185–193. [Google Scholar] [CrossRef] [PubMed]
  8. Lees, R.S.; Knols, B.; Bellini, R.; Benedict, M.Q.; Bheecarry, A.; Bossin, H.C.; Chadee, D.D.; Charlwood, J.; Dabire, R.K.; Djogbenou, L.; et al. Review: Improving our knowledge of male mosquito biology in relation to genetic control programmes. Acta Trop. 2014, 132, s2–s11. [Google Scholar] [CrossRef] [PubMed]
  9. Reisen, W.K.; Reeves, W.C. Bionomics and ecology of Culex tarsalis and other potential mosquito vector species. In Epidemiology and Control of Mosquito-Borne Arboviruses in California, 1943–1987; Reeves, W.C., Asman, S.M., Hardy, J.L., Milby, M.M., Reisen, W.K., Eds.; California Mosquito and Vector Control Association: Sacramento, CA, USA, 1990; pp. 254–329. [Google Scholar]
  10. Reeves, W.C.; Asman, S.M.; Hardy, J.L.; Milby, M.M.; Reisen, W.K. Epidemiology and Control of Mosquito-Borne Arboviruses in California, 1943–1987; California Mosquito and Vector Control Association, Inc.: Sacramento, CA, USA, 1990. [Google Scholar]
  11. Reisen, W.K. University of California—California Department of Public Health—Mosquito and Vector Control Association of California: Partners in arbovirus surveillance. Available online: http://www.mvcac.org/amg/wp-content/uploads/2011-MVCAC-Volume-79.pdf (accessed on 15 July 2016).
  12. Hribar, L.J. Influence and impact of mosquito-borne diseases on the history of Florida, USA. Life Excit. Biol. 2013, 1, 53–58. [Google Scholar] [CrossRef]
  13. Patterson, G. The Mosquito Wars: A History of Mosquito Control in Florida; University Press of Florida: Gainesville, FL, USA, 2004. [Google Scholar]
  14. Connelly, C.R.; Carlson, D.B. Florida Coordinating Council on Mosquito Control. In Florida Mosquito Control: The State of the Mission as Defined by Mosquito Controllers, Regulators, and Environmental Managers; Connelly, C.R., Carlson, D.B., Eds.; University of Florida: Vero Beach, FL, USA, 2009. [Google Scholar]
  15. Linthicum, K.; Smith, J.; Tabachnick, W. Mosquito control research. In Florida Mosquito Control: The State of the Mission as Defined by Mosquito Controllers, Regulators, and Environmental Managers; Connelly, C.R., Carlson, D.B., Eds.; University of Florida: Vero Beach, FL, USA, 2009; pp. 193–223. [Google Scholar]
  16. Bidlingmayer, W.L. The influence of environmental factors and physiological stage on flight patterns of mosquitoes taken in the vehicle aspirator and truck, suction, bait and New Jersey light traps. J. Med. Entomol. 1974, 11, 119–146. [Google Scholar] [CrossRef] [PubMed]
  17. Smith, J.P. The Florida contract mosquito control research program. Wing Beats 2009, 20, 18–21. [Google Scholar]
  18. Knight, R.L.; Walton, W.E.; O’Meara, G.F.; Reisen, W.K.; Wass, R. Strategies for effective mosquito control in constructed treatment wetlands. Ecol. Eng. 2003, 21, 211–232. [Google Scholar] [CrossRef]
  19. Provost, M.W. Tidal datum planes circumscribing salt marshes. Bull. Mar. Sci. 1976, 26, 558–563. [Google Scholar]
  20. Rey, J.R.; Rutledge, C.R. Mosquito Control Impoundments. Available online: http://desoto.ifas.ufl.edu/pdf/Insects/Mosquito%20Control%20Impoundments%20%20IN19200[1].pdf (accessed on 19 July 2016).
  21. Carlson, D.B.; O’Bryan, P.D. Mosquito production in a rotationally managed impoundment compared to other management techniques. J. Am. Mosq. Control Assoc. 1988, 4, 146–151. [Google Scholar] [PubMed]
  22. Carlson, D.B.; O’Bryan, P.D.; Rey, J.R. A review of current salt marsh management issues in Florida. J. Am. Mosq. Control Assoc. 1991, 7, 83–88. [Google Scholar] [PubMed]
  23. Rey, J.R.; Carlson, D.B.; Brockmeyer, R.E. Coastal wetland management in Florida: Environmental concerns and human health. Wetl. Ecol. Mgmt. 2012, 20, 197–211. [Google Scholar] [CrossRef]
  24. Brockmeyer, R.E., Jr.; Rey, J.R.; Virnstein, R.W.; Gilmore, R.G.; Earnest, L. Rehabilitation of impounded estuarine wetlands by hydrologic reconnection to the Indian River Lagoon, Florida (USA). Wetl. Ecol. Manag. 1996, 4, 93–109. [Google Scholar] [CrossRef]
  25. Carlson, D.B.; Indian River Mosquito Control District, Vero Beach, Florida, USA. Personal communication, 2016.
  26. Bonds, J.A.S. Ultra-low-volume space sprays in mosquito control: A critical review. Med. Vet. Entomol. 2012, 26, 121–130. [Google Scholar] [CrossRef] [PubMed]
  27. Mount, G.A.; Biery, T.L.; Haile, D.G. A review of ultralow-volume aerial sprays of insecticide for mosquito control. J. Am. Mosq. Control Assoc. 1996, 12, 601–618. [Google Scholar] [PubMed]
  28. Mount, G.A. A critical review of ultralow-volume aerosols of insecticide applied with vehicle-mounted generators for adult mosquito control. J. Am. Mosq. Control Assoc. 1998, 14, 305–334. [Google Scholar] [PubMed]
  29. Latham, M.D. Aerial adulticiding to control adult mosquitoes in Florida: 10 years of improvements in understanding and technology. Asp. Appl. Biol. 2008, 84, 281–288. [Google Scholar]
  30. Latham, M.; Barber, J. Mosquito control in Florida with a focus on aerial adulticiding. Outlooks Pest Manag. 2007, 18, 178–183. [Google Scholar] [CrossRef]
  31. Bonds, J.A.S.; Greer, M.J.; Fritz, B.K.; Hoffmann, W.C. Aerosol sampling: Comparison of two rotating impactors for field droplet sizing and volumetric measurements. J. Am. Mosq. Control Assoc. 2009, 25, 474–479. [Google Scholar] [CrossRef] [PubMed]
  32. Mount, G.A. Optimum droplet size for adult mosquito control with space sprays or aerosols of insecticides. Mosq. News 1970, 30, 70–75. [Google Scholar]
  33. Dukes, J.C.; Hallmon, C.F.; Shaffer, K.R.; Hester, P.G. Effects of pressure and flow rate on Cythion droplet size produced by three different ground ULV aerosol generators. J. Am. Mosq. Control. Assoc. 1990, 6, 279–282. [Google Scholar] [PubMed]
  34. Barber, J.; Greer, M.; Hewitt, A. A field measurement device for the aerosols used in mosquito control. Available online: http://johnwhock.com/wp-content/uploads/2013/06/FL-AM-Aerosol-Sampler-ASAE.pdf (accessed on 1 June 2016).
  35. Dukes, J.; Zhong, H.; Greer, M.; Hester, P.; Hogan, D.; Barber, J.A. A comparison of two spray nozzle systems used to aerially apply the ultra-low-volume adulticide fenthion. J. Am. Mosq. Control Assoc. 2004, 20, 27–35. [Google Scholar] [PubMed]
  36. Dukes, J.; Zhong, H.; Greer, M.; Hester, P.; Hogan, D.; Barber, J.A.S. A comparison of two ultra-low-volume spray nozzle systems by using a multiple swath scenario for the aerial application of fenthion against adult mosquitoes. J. Am. Mosq. Control Assoc. 2004, 20, 36–44. [Google Scholar] [PubMed]
  37. Hoffmann, W.C.; Walker, T.W.; Martin, D.E.; Barber, J.A.B.; Gwinn, T.; Smith, V.L.; Szumlas, D.; Lan, Y.; Fritz, B.K. Characterization of truck-mounted atomization equipment typically used in vector control 1. J. Am. Mosq. Control Assoc. 2007, 23, 321–329. [Google Scholar] [CrossRef]
  38. Linley, J.R.; Parsons, R.E.; Winner, R.A. Evaluation of ULV naled applied simultaneously against caged adult Aedes taeniorhynchus and Culicoides furens. J. Am. Mosq. Control Assoc. 1988, 4, 326–332. [Google Scholar] [PubMed]
  39. Moore, J.C.; Dukes, J.C.; Clark, J.R.; Malone, J.; Hallmon, C.F.; Hester, P.G. Downwind drift and deposition of malathion on human targets from ground ultra-low volume mosquito sprays. J. Am. Mosq. Control Assoc. 1993, 9, 138–142. [Google Scholar] [PubMed]
  40. Curtis, G.A.; Beidler, E.J. Influence of ground ULV droplet spectra on adulticide efficacy for Aedes taeniorhynchus. J. Am. Mosq. Control Assoc. 1996, 12, 368–371. [Google Scholar] [PubMed]
  41. Barber, J.A.; Greer, M.; Latham, M.; Stout, G. Canopy effects droplet size distribution and meteorological change. J. Am. Mosq. Control. Assoc. 2008, 24, 177–181. [Google Scholar] [CrossRef]
  42. Curtis, G.A.; Mason, J.A. Evaluation of equipment modifications and dosage rates of ground ULV applications of naled against Aedes taeniorhynchus in a Florida citrus grove. J. Am. Mosq. Control Assoc. 1988, 4, 345–350. [Google Scholar] [PubMed]
  43. Rathburn, C.B., Jr.; Dukes, J.C. A comparison of the mortality of caged adult mosquitoes to the size, number and volume of ULV spray droplets sampled in an open and a vegetated area. J. Am. Mosq. Control Assoc. 1989, 5, 173–175. [Google Scholar] [PubMed]
  44. Barber, J.A.S.; Greer, M.; Coughlin, J. Field tests of malathion and permethrin applied via a truck-mounted cold fogger to both open and vegetated habitats. J. Am. Mosq. Control Assoc. 2007, 23, 55–59. [Google Scholar] [CrossRef]
  45. Zhong, H. Aerial ultra-low-volume application of insecticide to control adult mosquitoes. In Encyclopedia of Pest Management; Pimentel, D., Ed.; CRC Press: Boca Raton FL, USA, 2007; Volume 2, pp. 4–6. [Google Scholar]
  46. Hester, P.G.; Shaffer, K.R.; Tietze, N.S.; Zhong, H.; Griggs, N.L. Efficacy of ground-applied ultra-low-volume malathion on honey bee survival and productivity in open and forest areas. J. Am. Mosq. Control Assoc. 2001, 17, 2–7. [Google Scholar] [PubMed]
  47. Zhong, H.; Dukes, J.; Greer, M.; Hester, P.; Shirley, M.; Anderson, B. Ground deposition impact of aerially applied fenthion on the fiddler crabs, Uca pugilator. J. Am. Mosq. Control Assoc. 2003, 19, 47–52. [Google Scholar] [PubMed]
  48. Zhong, H.; Latham, M.; Payne, S.; Brock, C. Minimizing the impact of the mosquito adulticide naled on honey bees, Apis mellifera (Hymenoptera: Apidae): Aerial ultra-low-volume application using a high-pressure nozzle system. J. Econ. Entomol. 2004, 97, 1–7. [Google Scholar] [CrossRef] [PubMed]
  49. Zhong, H.; Hribar, L.J.; Daniels, J.C.; Feken, M.A.; Brock, C.; Trager, M.D. Aerial ultra-low-volume application of naled: Impact on nontarget imperiled butterfly larvae (Cyclargus thomasi bethunebakeri) and efficacy against adult mosquitoes (Aedes taeniorhynchus). Environ. Entomol. 2010, 39, 1961–1972. [Google Scholar] [CrossRef] [PubMed]
  50. Qualls, W.A.; Xue, R.D.; Zhong, H. Impact of bifenthrin on honeybees and Culex quinquefasciatus. J. Am. Mosq. Control Assoc. 2010, 26, 223–225. [Google Scholar] [CrossRef] [PubMed]
  51. Latham, M. Aspects to consider for vector control. In Proceedings of the International Conference on Pesticide Application for Drift Management, Waikoloa, HI, USA, 27–29 October 2004; pp. 97–101.
  52. Latham, M.D.; Manatee County Mosquito Control District, Palmetto, Florida, USA. Personal communication, 2016.
  53. Chamberlain, R.W.; Sudia, W.D.; Coleman, P.H.; Beadle, L.D. Vector studies in the St. Louis encephalitis epidemic, Tampa Bay area, Florida, 1962. Am. J. Trop. Med. Hyg. 1964, 13, 456–461. [Google Scholar] [PubMed]
  54. Day, J.F. Predicting St. Louis encephalitis virus epidemics: Lessons from recent, and not so recent, outbreaks. Annu. Rev. Entomol. 2001, 46, 111–138. [Google Scholar]
  55. Day, J.F.; Tabachnick, W.J.; Smartt, C.T. Factors that influence the transmission of West Nile virus in Florida. J. Med. Entomol. 2015, 52, 743–754. [Google Scholar] [CrossRef] [PubMed]
  56. Day, J.F. Disease surveillance, outbreaks and control in Florida. In Florida Mosquito Control: The State of the Mission as Defined by Mosquito Controllers, Regulators, and Environmental Managers; Connelly, C.R., Carlson, D.B., Eds.; University of Florida: Vero Beach, FL, USA, 2009; pp. 131–144. [Google Scholar]
  57. Day, J.F.; Shaman, J. Mosquito-borne arboviral surveillance and the prediction of disease outbreaks. In Flavivirus Encephalitis; Ruzek, D., Ed.; InTech: Rijeka, Croatia, 2011; pp. 105–130. [Google Scholar]
  58. Day, J.F.; Shaman, J. Severe winter freezes enhance St. Louis encephalitis virus amplification and epidemic transmission in peninsular Florida. J. Med. Entomol. 2009, 46, 1498–1506. [Google Scholar] [PubMed]
  59. Shaman, J.; Day, J.F.; Stieglitz, M.; Zebiak, S.; Cane, M. An ensemble seasonal forecast of human cases of St. Louis encephalitis in Florida based on seasonal hydrologic forecasts. Clim. Chang. 2006, 75, 495–511. [Google Scholar] [CrossRef]
  60. Day, J.F.; Curtis, G.A. When it rains, they soar—And that makes Culex nigripalpus a dangerous mosquito. Am. Entomol. 1994, 40, 162–167. [Google Scholar] [CrossRef]
  61. Shaman, J.; Day, J.F.; Stieglitz, M. Drought-induced amplification and epidemic transmission of West Nile virus in southern Florida. J. Med. Entomol. 2005, 42, 134–141. [Google Scholar] [CrossRef] [PubMed]
  62. Day, J.F.; Shaman, J. Using hydrologic conditions to forecast the risk of focal and epidemic arboviral transmission in peninsular Florida. J. Med. Entomol. 2008, 45, 458–465. [Google Scholar] [CrossRef]
  63. Detinova, T.S. Age-grouping Methods in Diptera of Medical Importance; World Health Organization: Geneva, Switzerland, 1962. [Google Scholar]
  64. Polovodova, V.P. The determination of the physiological age of female Anopheles by the number of gonotrophic cycles completed. Med. Parazitol. Parazit. Bolezn. 1949, 18, 352–355. [Google Scholar]
  65. Tabachnick, W.J. Arthropods and pathogens: Issues for emerging diseases. In Emerging Infections; Krause, R.M., Ed.; Academic Press: New York, NY, USA, 1998; pp. 411–429. [Google Scholar]
  66. Tabachnick, W.J. Reflections on the Anopheles gambiae genome sequence, transgenic mosquitoes and the prospect for controlling malaria and other vector borne diseases. J. Med. Entomol. 2003, 40, 597–606. [Google Scholar] [CrossRef] [PubMed]
  67. Tabachnick, W.J. Challenges in predicting climate and environmental effects on vector-borne disease episystems in a changing world. J. Exp. Biol. 2010, 213, 946–954. [Google Scholar] [CrossRef] [PubMed]
  68. Tabachnick, W.J.; Day, J.F. Impact of climate change on vector-borne arboviral episystems. In Viral Infections and Global Change; Singh, S.K., Ed.; John Wiley and Sons: Hoboken, NJ, USA, 2014; pp. 21–34. [Google Scholar]
  69. Tabachnick, W.J. Climate change and arboviruses: Lessons from the evolution of the yellow fever and dengue viruses. Annu. Rev. Virol. 2016, in press. [Google Scholar] [CrossRef] [PubMed]
  70. Benelli, G. Research in mosquito control: Current challenges for a brighter future. Parasitol. Res. 2015, 114, 2801–2805. [Google Scholar] [CrossRef] [PubMed]
  71. Ooi, E.E.; Goh, K.T.; Gubler, D.J. Dengue prevention and 35 years of vector control in Singapore. Emerg. Infect. Dis. 2006, 12, 887–893. [Google Scholar] [CrossRef] [PubMed]
  72. Morrison, A.C.; Zielinski-Gutierrez, E.; Scott, T.W.; Rosenberg, R. Defining challenges and proposing solutions for control of the virus vector Aedes aegypti. PLoS Med. 2008, 5, e68. [Google Scholar] [CrossRef] [PubMed]
  73. Araújo, H.R.; Carvalho, D.O.; Ioshino, R.S.; Costa-da-Silva, A.L.; Capurro, M.L. Aedes aegypti control strategies in Brazil: Incorporation of new technologies to overcome the persistence of dengue epidemics. Insects 2015, 6, 576–594. [Google Scholar] [CrossRef] [PubMed]
  74. Alfonso-Sierra, E.; Basso, C.; Beltrán-Ayala, E.; Mitchell-Foster, K.; Quintero, J.; Cortés, S.; Manrique-Saide, P.; Guillermo-May, G.; Caprara, A.; Carvalho de Lima, E.; et al. Innovative dengue vector control interventions in Latin America: What do they cost? Pathog. Glob. Health 2016, 110, 14–24. [Google Scholar] [CrossRef] [PubMed]
  75. Bowman, L.R.; Donegan, S.; McCall, P.J. Is dengue vector control deficient in effectiveness or evidence?: Systematic review and meta-analysis. PLoS Negl. Trop. Dis. 2016, 10, e0004551. [Google Scholar] [CrossRef] [PubMed]
Figure 1. (a) A mosquito impoundment not connected to the adjacent Florida Indian River Lagoon resulting in the loss of the wetland vegetation; (b) A mosquito impoundment reconnected to the adjacent Florida Indian River Lagoon and maintained using Rotational Impoundment Management (RIM) resulting in restoration of wetland vegetation (Courtesy of Douglas B. Carlson).
Figure 1. (a) A mosquito impoundment not connected to the adjacent Florida Indian River Lagoon resulting in the loss of the wetland vegetation; (b) A mosquito impoundment reconnected to the adjacent Florida Indian River Lagoon and maintained using Rotational Impoundment Management (RIM) resulting in restoration of wetland vegetation (Courtesy of Douglas B. Carlson).
Insects 07 00050 g001
Figure 2. (a) An aerial adulticiding mission using fogging (Courtesy of G. Alan Curtis); (b) An aerial adulticiding mission using ultra-low volume (ULV) (Courtesy of Mark D. Latham).
Figure 2. (a) An aerial adulticiding mission using fogging (Courtesy of G. Alan Curtis); (b) An aerial adulticiding mission using ultra-low volume (ULV) (Courtesy of Mark D. Latham).
Insects 07 00050 g002
Figure 3. Criteria for successful aerial and vehicle ULV adulticiding (Courtesy of Mark D. Latham).
Figure 3. Criteria for successful aerial and vehicle ULV adulticiding (Courtesy of Mark D. Latham).
Insects 07 00050 g003
Figure 4. (a) A hydrological map for south Florida showing the ground water table during a one-week period in 2010; (b) A risk map for West Nile in Florida based on this hydrological information, models, and knowledge about reservoirs, vectors, and virus amplification and high-risk regions for WNV transmission (Courtesy of Jonathan F. Day).
Figure 4. (a) A hydrological map for south Florida showing the ground water table during a one-week period in 2010; (b) A risk map for West Nile in Florida based on this hydrological information, models, and knowledge about reservoirs, vectors, and virus amplification and high-risk regions for WNV transmission (Courtesy of Jonathan F. Day).
Insects 07 00050 g004
Figure 5. The epidemic signature of rainfall and drought events for WNV and SLEV transmission in Florida. MWTD, modeled water table depth (Courtesy of Jonathan F. Day).
Figure 5. The epidemic signature of rainfall and drought events for WNV and SLEV transmission in Florida. MWTD, modeled water table depth (Courtesy of Jonathan F. Day).
Insects 07 00050 g005
Table 1. Peer reviewed publications from Florida Medical Entomology Laboratory (FMEL) and Public Health and Entomology Research and Education Center (PHEREC) since 1960 on selected Florida mosquitoes, arboviruses, and related subjects with the total number of articles produced on these subjects (Data from PubMed as of 20 July 2016).
Table 1. Peer reviewed publications from Florida Medical Entomology Laboratory (FMEL) and Public Health and Entomology Research and Education Center (PHEREC) since 1960 on selected Florida mosquitoes, arboviruses, and related subjects with the total number of articles produced on these subjects (Data from PubMed as of 20 July 2016).
TopicTotal Publications Since 1960PHERECFMEL% of Total by FMEL and PHEREC
Culex nigripalpus19726534
Florida mosquito ecology7712635
Florida mosquito control392427329
Florida St. Louis encephalitis9014248
Florida West Nile11613733
Florida Aedes aegypti23228337
Florida mosquito pesticides141301532
Florida Aedes4362012333
Florida Culex2352610957

Share and Cite

MDPI and ACS Style

Tabachnick, W.J. Research Contributing to Improvements in Controlling Florida’s Mosquitoes and Mosquito-borne Diseases. Insects 2016, 7, 50. https://doi.org/10.3390/insects7040050

AMA Style

Tabachnick WJ. Research Contributing to Improvements in Controlling Florida’s Mosquitoes and Mosquito-borne Diseases. Insects. 2016; 7(4):50. https://doi.org/10.3390/insects7040050

Chicago/Turabian Style

Tabachnick, Walter J. 2016. "Research Contributing to Improvements in Controlling Florida’s Mosquitoes and Mosquito-borne Diseases" Insects 7, no. 4: 50. https://doi.org/10.3390/insects7040050

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