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BIOLOGICAL CONTROL OF MOSQUITOES

Culex , Aedes, Anopheles, etc. -- Diptera, Culicidae

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Introduction

 

Detailed Biological Control Measures

 

References

 

[Please refer also to Related Research #1, #2, #3 ]

 

 

Introduction

 

Interest in biological control of medical pests and vectors had its modest beginning prior to the turn of the last century (Lamborn 1890).  At that time the possible use of dragonflies as natural enemies for the control of mosquitoes was clearly recognized.  However, as is true even today, the enormous difficulties associated with the colonization and management of these insects quickly extinguished any idea for the practical use of these predators for mosquito control.  Shortly after the turn of the century the mosquitofish, Gambusia affinis (Baird & Girard), came to the forefront of biological control.  This small fish, being much easier to deal with than dragonflies, was quickly utilized and transported throughout the world during the early decades of this century in attempts to control mosquitoes.

 

The Mosquitofish, G. affinis, <PHOTO> along with several other natural controls, was employed with some enthusiasm during the first 40 years of the century.  All of these control measures were curtailed sharply with the introduction of synthetic organic insecticides after World War II.  The convenience and quick killing power of these chemicals was so dramatic for such insects as mosquitoes, flies and lice, that other control tactics were quickly reduced to a minor role.  Nevertheless, interest in alternative methods of control, especially biological, was to arise again when the succession of chemicals developed during the 1940s and 1950s began to fail due to the development of widespread genetic resistance in vector and pest populations.  Although the biological control of medically important pests and vectors has made some progress since its revival, it has been rather slow and is still well behind that which has occurred in agricultural systems (Service 1983).  This disparity is partly due to the problems of fixing pest tolerance levels, but more importantly because of the temporary unstable habitats exploited by medically important pests (Legner & Sjogren 1984, Legner & Warkentin 1989).

 

As Service (1983) pointed out, the successful widespread use of biological control agents against mosquitoes will require a much better understanding of the ecology of predator/prey and pathogen/host relationships.  The opportunistic characteristics of many species (i.e., their ability to exploit temporary habitats, coupled with their short generation time, high natural mortality, great dispersal potential, and other R-strategist characteristics) pose difficult problems for any biotic regulatory mechanism.  Mosquitoes, in general, exploit a wide breadth of different aquatic habitats.  Consequently, under many conditions a biological control agent will have a much narrower range of environmental activity than that of the target species.  Thus, in many situations a number of different biological control agents and/or appropriate methods will be necessary if we expect to control even a single species of mosquito across its range of exploitable breeding sources.

 

The most important nonarthropod invertebrate predators to draw attention for mosquito control are the turbellarian flatworms and a coelenterate.  Flatworm species which were shown experimentally to be excellent predators of mosquito larvae in a variety of aquatic habitats are Dugesia dorotocephala (Woodworth) and Dugesia tigrina (Girard) (Legner & Medved 1974  , Yu & Legner  1976, Collins & Washino 1978, Case & Washino 1979, Legner 1977 , 1979, Ali & Mulla 1983, George 1978, Meyer 1981a,b; George et al. 1983).  Several biological and ecological attributes of flatworms would seem to make them ideal candidates for manipulative use.  Among them are ease of mass production, an overwintering embryo, effective predatory behavior in shallow waters with emergent vegetation, on site exponential reproduction following inoculation (Medved & Legner 1974, Tsai & Legner 1977, Legner & Tsai 1978, Legner 1979) and tolerance to environmental contaminants (Levy & Miller 1978, Nelson 1979).

 

Collins & Washino (1978) and Case & Washino (1979) suggested that flatworms, particularly Mesostoma, may play an important role in the natural regulation of mosquitoes in some California rice fields because of their densities and their predatory attack on mosquito larvae in sentinel cages (Garcia & Legner 266.  99 ).  Preliminary analysis using extensive sampling showed a significant negative correlation between the presence of flatworms and population levels of Cx. tarsalis and An. freeborni (Case & Washino 1979).  However, these workers cautioned that an alternative hypothesis related to the ecology of these species may have accounted for the correlations.  Later investigations by Palchick & Washino (1984), employing more restrictive sampling, were unable to confirm the correlations between Mesostoma and mosquito populations.  However, the enormity of the problem associated with sampling in California rice fields, coupled with the complexity of the prey and predator interactions (Collins & Washino 1979), make further studies necessary before the role of this group of flatworms in rice fields can be clearly established.

 

Nevertheless, in a detailed study by Legner (1977), which was later duplicated by Ali & Mulla (1983), the relationship between the number of Dugesia dorotocephala applied per m2 of water surface and the average density of mature Culex spp. larvae was highly significant and lineal, the latter assuming densities of <1 per standard dipper at the higher Dugesia application rates.  It was emphasized that the use of D. dorotocephala for direct mosquito suppression as an alternative to insecticides or Gambusia is desirable because natural predator densities appeared unaffected, and a single application resulted in a prolonged and increased suppression of mosquito larvae as the planarians reproduced in the environments to which they had been introduced.  Although D. dorotocephala is widespread in North America (Kenk 1972, McConnell 1967), some strains are very cannibalistic and might be unsuitable for mass rearing.  The production of adequate numbers of the noncannibalistic strain is possible if cultures are stockpiled during winter months (Legner et al. 1976) and rapid mass production can be obtained through carefully controlled culture with filtration, optimum temperature and dissolved oxygen and food (Legner et al. 1976, Tsai & Legner 1977, Legner & Tsai 1978).  Progeny require about one month to reach maturity.

 

The important attributes for manipulative use of flatworms mentioned above raises the question of why they have not been developed further for use in mosquito control.  Perhaps the contemporary development of Bacillus thuringiensis var. israelensis DeBarjac (H-14), a highly selective easily applied microbial insecticide, may have been at least partially responsible for slowing further work and development of these predators.  Their mass culture must be continuous and demands skilled technical assistants (Legner & Tsai 1978).  Their persistence in field habitats may also depend on the presence of other organisms that can be utilized for food during low mosquito abundance, such as ostracods (Legner et al. 1976).

 

The coelenterates, like the flatworms, showed great promise for further development and use in selected breeding habitats.  Chlorohydra viridissima (Pallas) is efficient in suppressing culicine larvae in ponds with dense vegetation and this species also can be mass produced (Lenhoff & Brown 1970, Yu et al. 1974a, 1974b. 1975).  However, like the flatworms, work on these predators has waned, perhaps for similar reasons as speculated for the flatworms.  Microbial pesticides can be employed over an extensive range of different mosquito breeding habitats.  Also, commercial production of flatworms and coelenterates would be much more costly, and storage of viable cultures all but impossible.

 

Recent emphasis on the fungal genus Lagenidium which is capable of infecting and killing several genera of mosquito larvae (e.g., Anopheles, Culex, Aedes, and Psorophora) encourages the continued quest for biological control agents as alternatives to pesticides (McCray et al. 1973, Christensen et al. 1977, Glenn & Chapman 1978,  Washino & Fukushima 1978, Washino 1981, Axtell et al. 1982, Domnas et al. 1982, Jaronski & Axtell 1982, 1983a,b).  The potential of such fungi for operational mosquito control is nevertheless no greater than for some of the flatworms or hydra.  This recent switch in attention to fungi is probably due to the existence of a greater number of mycologists in the research force than specialists in the other groups.  Problems of mass production, dissemination of an acceptable fungal stage and adaptability to polluted water habitats have placed their immediate deployment in doubt.  Similar problems were either nonexistent or minimal with the Dugesia flatworms, so that their integrity as effective and available biological control agents is undiminished.

 

The successful widespread use of biological control agents against mosquitoes will require a much better understanding of the ecology of predator/prey and pathogen/host relationships (Service 1983).  The opportunistic characteristics of many species (i.e., their ability to exploit temporary habitats, coupled with their short generation time, high natural mortality, great dispersal potential, and other R-strategist characteristics) pose difficult problems for any biological control agent.  Mosquitoes typically exploit many aquatic habitats.  Often a biological control agent will have a much narrower range of environmental activity than the target species.  Thus, in many situations a number of different biological control agents and/or appropriate methods will be necessary to control even one species of mosquito across its range of exploitable breeding sources.

 

Detailed Biological Control Measures

 

Fish.--Several species of fishes are used for the biological control of mosquitoes, and these species together form the major successes in biological control.  Unfortunately, their usefulness is limited to more permanent bodies of water, and even under these situations their impact on the target species has been only partially successful.  Bay et al (1976) point out that many species of fish consume mosquito larvae, but only a few species have been manipulated to manage mosquito populations.  [Please see Research]

 

The mosquitofish, G. affinis, <PHOTO> is the best known agent for mosquito control.  This fish, which is native to the southeastern United States, eastern Mexico and the Caribbean area, was first used as an introduced agent for mosquito control when it was transported from North Carolina to New Jersey in 1905 (Lloyd 1987).  Shortly thereafter it was introduced to the Hawaiian Islands to control mosquitoes which had been introduced during the 19th century.  During the next 70 years, the mosquitofish was transported to over 50 countries and today stands as the most widely disseminated biological control agent (Bay 1969, Lloyd 1987).  Many of these introductions were aimed at Anopheles species that were transmitting malaria.  Hackett (1937) described its usefulness in malaria control programs in Europe.  He commented that its effects were not sufficient by themselves, but that the fish had a definite impact on the suppression of the disease.  Tabibzadeh et al. (1970) reported a rather extensive release program in Iran and concluded that the fish was an important component in malaria eradication.  Sasa and Kurihara (1981) and Service (1983) believed that the fish had little impact on the disease and that most evidence is circumstantial.  Gambusia no longer is recommended by the World Health Organization for malaria control programs, primarily because of its harmful impact on indigenous species of fish (Service 1983, Lloyd 1987).

 

The biological attributes of G. affinis, namely a high reproductive capability, high survivorship, small size, omnivorous foraging in shallow water, relatively high tolerance to variations in temperature, salinity and organic waste, would seemingly make this species an excellent biological control agent (Bay et al. 1976, Moyle 1976).  However, whether this fish leads to effective mosquito control at practical costs in many situations is still debated.  Kligler's (1930) statement that "... their usefulness as larvae-destroyers under local conditions where vegetation is abundant and micro fauna rich enough to supply their needs without great trouble, is limited.  In moderately clear canals, on the other hand, or in pools having a limited food supply, they yielded excellent results ..." is probably one of the most accurate.

 

In California this fish had been used extensively for control of mosquitoes in various habitats (Bay et al. 1976).  Many mosquito abatement districts in the State have developed systems for culturing, harvesting and winter storage of the mosquito fish to have enough available for planting early in the spring (Coykendall 1980).  This is particularly important in the rice growing areas of California where early stocking appears to be of critical importance for build-up of fish populations to control mosquitoes during late summer.  The results of the use of G. affinis in California rice fields will be summarized below as an illustrative example of the mixed successes achieved in the field.

 

Rice cultivation in California continuously poses one of the most difficult control problems for Anopheles and Culex species.  Hoy & Reed (1970) showed that good to very good control of Culex tarsalis Coquillett could be achieved at stocking rates of about 480 or more females per hectare, and Stewart et al (1983) reported excellent control with a similar stocking rate against this species in the San Joaquin Valley.

 

Although Cx. tarsalis appears to be controlled effectively by G. affinis, the control of its frequent companion in northern California rice fields, Anopheles freeborni Aitken, is less apparent.  Hoy et al. (1971) showed a reduction of An. freeborni populations at various stocking rates of about 120 to 720 fish per hectare, but the reduction was not nearly as striking as for Cx. tarsalis.  These workers surmised that improvement in control could be achieved by earlier season stocking, possibly multiple release points in fields and a reliable source of healthy fish for stocking.  Despite an extensive research effort in mass culture, management and storage for G. affinis by the State of California (Hoy & Reed 1971), a mass production method has not been satisfactorily achieved (Downs et al. 1986, Cech and Linden 1987).

 

Studies of G. affinis for control of mosquitoes in wild rice show that relatively high stocking rates can effectively reduce An. freeborni and Cx. tarsalis populations within a three-month period (Kramer et al. 1987a).  The commercial production of wild rice, which is a more robust and toller plant than white rice and requires only 90 instead of 150 days to mature, has been increasing over the last few years in California (Kramer et al. 1987).  In the above study, stocking rates of 1.7 Kg/ha (ca. 2400 fish/Kg) released in 1/10 ha wild rice plots failed to show a significant difference in reduction of mosquitoes from plots with no fish.  A decrease in numbers of larvae was noted just prior to harvest which suggested that the fish were beginning to have an impact on mosquito numbers (Kramer et al. 1987).  Numbers of fish in these plots, based on recovery after drainage, was about 100,000 individuals per hectare (ca. 32 Kg/ha) or a density of about 10 fish per square meter.  However, significant control was not achieved.

 

During 1987 this study was repeated at the rates of 1.7 and 3.4 Kg/ha of fish.  Results showed an average suppression of larvae (primarily An. freeborni) of <1 and 0.5 per dip for the low and high rate respectively, compared to control plots which averaged >4.5 per dip.  Fish densities in the 1987 study surpassed those of 1986 by about two fold at the 1.7 Kg/ha rate and three fold at the 3.4 Kg/ha rate.  It is believed that these greater fish numbers accounted for the control differences observed in the second year, although mosquitoes were not eliminated.  Differences between test plots and control plots were first observed eight weeks after the fish had been planted and mosquitoes remained under control until drainage of the fields (Kramer et al. 1988).

 

Davey & Meisch (1977a,b) showed that the mosquitofish at inundative release rates of 4,800 fish per hectare, was effective for control of Psorophora columbiae (Dyar & Knab) in Arkansas rice fields.  Fish released at the water flow inlets dispersed quickly throughout the fields.  This is an important attribute for controlling species of Psorophora and Aedes, whose hatch and larval development are completed within a few days.  A combination of 1,200 G. affinis and about 300 sunfish (Lepomis cyanellus Rafinesque) gave better control than either four times the amount of G. affinis or L. cyanellus used separately.  This synergistic effect reduces logistic problems associated with having enough fish available at the times fields are inundated.  Blaustein (1986) found enhanced control of An. freeborni by mosquitofish in California rice fields after the addition of green sunfish.  He speculated that the increased control was the result of the mosquitofish spending more time in protected areas where mosquitoes were more abundant and the green sunfish was avoided.  The availability of fish for stocking fields either inundatively, such as in Arkansas or for control later in the season as practiced in California, has been a fundamental reason why fish have not been used more extensively in rice fields.

 

A unique use of the mosquitofish by inundative release was reported by Farley & Caton (1982).  The fish were released in subterranean urban storm drains to control Culex quinquefasciatus Say breeding in entrapped water at low points in the system.  Fish releases were made following the last major rains to avoid having them flushed out of the system.  Fish survived for more than three months during the summer and were found throughout the system.  Gravid females produced progeny.  However, no mating occurred, and after the initial increase in numbers populations of fish diminished as summer progressed.  Reductions of mosquitoes from 75 to 94% were observed for three months compared to untreated areas (Mulligan et al. 1983).  This control practice is now conducted on a routine basis by the Fresno Mosquito Abatement District (J. R. Caton 1987, pers. comm.).

 

              Although G. affinis has been useful for control of mosquitoes in a number of situations, clearly there are drawbacks to its use.  In fact, if today's environmental awareness existed at the turn of the century, this fish probably never would have been intentionally introduced into exotic areas (Pelzman 1975, Lloyd 1987).  The major objection to this fish has been its direct impact on native fishes through predation, or its indirect impact through competition (Bay et al. 1976, Schoenherr 1981, Lloyd 1987).  More than 30 species of native fish have been adversely affected by the introduction of Gambusia (Schoenherr 1981, Lloyd 1987).  Gambusia, a general predator, can also substantially reduce zooplankton and thus lead to algal blooms in certain situations (Hurlbert et al. 1972).  Introductions of Gambusia have also reduced numbers of other aquatic invertebrates coinhabiting the same waters (Hoy et al. 1972, Farley & Younce 1977, Rees 1979, Walters & Legner 1980, Hurlbert & Mulla 1981).  In California where native pup fishes in the genus Cyprinodon  (PHOTO-1,  #2 )  may afford a greater potential for mosquito control under a wider range of environmental stresses than Gambusia (Walters & Legner 1980), the California Department of Fish and Game has discouraged their use on the basis that unknown harmful effects might result to other indigenous fishes. There is also the concern that certain rare species of Cyprinodon might be lost through hybridization.

 

The next most widely used fish for mosquito control is the common guppy, Poecilia reticulata (Peters) <PHOTO>.  It has been deployed successfully in Asia for the control of waste water mosquitoes, especially Cx. quinquefasciatus.  Like its poeciliid relative Gambusia, it is native to the Americas (tropical South America).  But, rather than being intentionally introduced to control mosquitoes, it was taken to other parts of the world by tropical fish fanciers.  Sasa et al. (1965) observed wild populations of this fish breeding in drains in Bangkok and concluded from their observations that it was controlling mosquitoes common to that habitat.  The practical use of guppies is primarily restricted to subtropical climates because of an inability to tolerate temperate-zone water temperatures (Sasa & Kurihara 1981).  However, their most important attribute is a tolerance to relatively high levels of organic pollutants, which makes them ideal for urban water sources that are rich in organic wastes.  In Sri Lanka, wild populations have been harvested and used for the control of mosquitoes in abandoned wells, coconut husk pits and other sources rich in organics (Sasa & Kurihara 1981).  The fish occursin in India, Indonesia and China and has been intentionally introduced for filariasis control into Burma (Sasa & Kurihara 1981).  Mian et al (1985) evaluated its use for control of mosquitoes in sewage treatment facilities in southern California and concluded that guppies showed great potential for mosquito control in these situations.

 

Exotic fish have also been used for clearing aquatic vegetation from waterways which has resulted in excellent mosquito control.  In the irrigation systems of southeastern California, three species of subtropical cichlids, Tilapia zillii (Gervais), Oreochromis mossambica (Peters) and Oreochromis hornorum (Trewazas) <PHOTO> were introduced and have become established over some 2,000 ha of Cx. tarsalis breeding habitat (Legner & Sjogren 1984).  In this situation, mosquito populations are under control by a combination of direct predation and the consumption of aquatic plants by these omnivorous fishes (Legner & Medved 1973, Legner 1978a,  1983; Legner & Fisher 1980; Legner & Murray 1981, Legner & Pelsue 1983).  As Legner & Sjogren (1984) indicate, this is a unique example of persistent biological control and probably only applicable for relatively sophisticated irrigations systems where a permanent water supply is assured, and water conditions are suitable to support the fish (Legner et al. 1980).  There is a three-fold advantage in the use of these fish:  (1) clearing of vegetation to keep waterways open, (2) mosquito control and (3) a fish large enough to be caught for human consumption.  Some sophistication is necessary when stocking these cichlids for aquatic weed control, which is often not understood by irrigation districts personnel (Hauser et al. 1976, 1977; Legner 1978b).  Otherwise competitive displacement may eliminate T. zillii, <PHOTO> the most efficient weed consuming species (Legner 1986).

 

Household storage of water in open containers has frequently been the cause for outbreaks of human disease transmitted by Aedes aegypti (Linnaeus) in less developed parts of the world.  While conducting Ae. aegypti surveys in Malaysia during the mid 1960s, Dr. Richard Garcia of UC Berkeley observed what were apparently P. reticulata being utilized by town residents for the control of mosquitoes in bath and drinking water storage containers.  The origin of this control technique was not clear but it appeared to be a custom brought to the area by Chinese immigrants.  Not all residents used fish, but those that did had no breeding populations of Ae. aegypti.

 

Neng (1987) reported on the use of a catfish, Claris sp., for the control of Ae. aegypti in water storage tanks in coastal villages of southern China.  This fish was considered appropriate since it was indigenous, edible, consumed large numbers of mosquito larvae, had a high tolerance for adverse conditions and could be obtained from the local markets.  One fish was placed in each water source and later checked for its presence by larval survey teams about every 10 to 15 days.  If fish were not found on inspection the occupant was told to replace the fish or be fined.  The investigation was conducted from 1981 to 1985, and surveys over this period showed a sharp initial reduction in Ae. aegypti followed by a low occurrence of the mosquito over the four-year study period.  Outbreaks of dengue were observed in neighboring provinces during this period, but not in the fishing villages under observation.  The cost of the program was estimated to be about 1/15 that of indoor house spraying (Neng 1987).

 

Alio et al. (1985) described another use of a local species of fish for the control of a malaria vector similar to the method reported by Kligler (1930).  Oreochromis sp., a tilapine, was introduced into human-made water catchment basins called "barkits" in the semi arid region of northern Somalia.  These small scattered impoundments served as the only sources of water during the dry season for the large pastoral population of the area.  Anopheles arabiensis Patton, the vector of malaria in that area, is essentially restricted to these sites.  Release of fish into the "barkits" dramatically reduced both the vector and nonvector populations of mosquitoes rather quickly.  Treatment of the human population with antimalarial drugs during the initial phase of this two-year study, combined with the lower vector population reduced the transmission rate of malaria to insignificance over a 21 month period whereas the control villages remained above 10 percent.  Alio et al (1985) commented that the local population also recognized the added benefits of reduced vegetation and insects in the water sources.  This resulted in community cooperation and was expected to further benefit the control strategy by providing assistance in fish distribution and maintenance as the program expanded to other areas. 

 

The last two examples involve the use of indigenous over exotic fish where feasible in vector control programs.  There are other examples where native fishes have been used in specialized circumstances (Kligler 1930, Legner et al. 1974, Menon & Rajagopalan 1978, Walters & Legner 1980 , Ataur-Rahim 1981 and Luh 1981).  Lloyd (1987) argued that only indigenous fish should be employed for mosquito control because of the environmental disruption induced by exotics such as G. affinis.  However, he suggested that native fish should be analyzed carefully for prey selectivity, reproductive potential and effectiveness in suppression pest populations before attempting their use.  Lloyd (1987) also pointed out that a multidisciplinary approach involving fisheries biologists and entomologists should be employed when developing indigenous fish for mosquito control.  However, in California where native pup fishes in the genus Cyprinodon  <PHOTO>  may afford a greater potential for mosquito control under a wider range of environmental stresses than Gambusia (Walters & Legner 1980 ), the California Department of Fish and Game discourages their use on the basis that unknown harmful effects might result to other indigenous fishes.  There is also the concern that certain rare species of Cyprinodon might be lost through hybridization.

 

Perhaps China's example of a multipurpose use of native fish for mosquito control and a human protein source is the most resourceful strategy.  This application for mosquito control is not new.  Kligler (1930) used a tilapine fish to control Anopheles sp. in citrus irrigation systems in old Palestine, where farmers cared for the fish, consuming the larger ones.  According to Luh (1981), the culture of edible fish for the purpose of mosquito control and human food is not widely encouraged in China.  The old Chinese peasant custom of raising edible fish in rice fields has received greater attention in recent times because of the benefits made possible through this practice.  The common carp, Cyprinus carpio Linnaeus, and the grass carp, Ctenopharygodon idella Valenciennes, are most commonly used.  Fish are released as fry at the time rice seedlings are planted.  Fields are specially prepared with a central "fish pit" and radiating ditches for refuge when water levels are low.  Pisciculture in rice fields, as noted by Luh (1981), has three major benefits:  (1) a significant reduction in culicine and to a lesser extent anopheline larvae, (2) fish are harvested as food and (3) rice yields are increased apparently by a reduction in competitors and possibly by fertilization of the plants by fish excreta.

 

Another group of fishes, the so-called "instant" or annual fishes, (Cyprinodontidae), which are native to South America and Africa, have been considered as possible biological control agents for mosquitoes (Vanderplant 1941, 1967; Hildemann & Wolford 1963; Bay 1965, 1972; Markofsky & Matias 1979).  The relatively drought resistant eggs of these cyprinodontids, which allows them to utilize temporary water sources as habitat, would seem to make them ideal candidates for mosquito control.  There is also some evidence that they do impact mosquito populations in native areas (Vanderplant 1941, Hildemann & Wolford 1963, Markofsky & Matias 1979).  Research on the biology and ecology of several species has been conducted; however, there are no published accounts on the successful use of these fish in field situations.  In California the South American species Cynolebias nigripinnis Regan and Cynolebias bellottii (Steindachner) <PHOTO>, survived the summer in rice fields, but no reproduction was observed over a three-year period (Coykendall 1980).  It was speculated that they may play a future role in California's mosquito control program in temporary pools and possibly rice fields.  C. bellottii was observed to reproduce repeatedly and to persist in small intermittently dried ponds in Riverside, California for eleven consecutive years, 1968-1979 (Legner & Walters unpubl.).  Four drying flooding operations over two months were required to eliminate this species from ponds that were to be used for native fish studies (Walters & Legner 1980 ).  It seems logical, given the biological capability of surviving an annual dry period, that these fish could be successfully integrated into mosquito control programs, especially in newly created sources in geographic areas where they naturally occur (Vaz-Ferreira et al. 1963, Anon 1981, and Geberich 1985).

 

Arthropods.--Numerous species of predatory arthropods have been observed preying on mosquitoes, and in some cases are believed to be important in controlling mosquitos (James 1964, Service 1977, Collins & Washino 1979, McDonald & Buchanan 1981).  However, among the several hundred predatory species observed, only a few have been used in a manipulative way to control mosquitoes.  Dragonflies, sometimes referred to as mosquito hawks, were one of the first arthropods to be examined.  Difficulties in colonization, production and handling have restricted their use to experimental observation.  It is unlikely that they will ever be used extensively (Lamborn 1890, Beesley 1974, El Rayah 1975, Riviere et al. 1987a).

 

There are a few cases where the difficulties associated with the manipulative use of arthropods have been at least partly overcome.  More than 50 years ago, in a classic use of biological control, the mosquito Toxorhynchites, whose larvae are predators of other mosquitoes, was released on several Pacific Islands in an effort to control natural and artificial container breeding mosquitoes such as Ae. aegypti and Aedes albopictus (Skuse) (Paine 1934, Bonnet & Hu 1951, Petersen 1956).  The releases were not considered successful, but the mosquitoes did establish in some areas (Steffan 1975).  Several reasons to explain why these releases failed were low egg production, lack of synchrony between predator and prey life cycles, and selection of only a relatively small number of prey breeding sites (Muspratt 1951, Nakagawa 1963, Trpis 1973, Bay 1974, Riviere 1985).

 

Although not apparently a suitable predator in the classical sense, there is still interest in the use of various Toxorhynchites spp. for inundative release (Gerbert & Visser 1978).  Trpis (1981) working with Toxorhynchites brevipalpis (Theobald) showed that the high daily consumption rate and long survival of the larvae without prey made it a prime candidate for biological control use.  Observations on adult females indicated a 50% survivorship over a 10-week period with a relatively high oviposition rate per female.  All the above attributes suggest that this species would be useful for inundative release programs against container breeding mosquitoes.  Studies by Focks et al (1979) in Florida, working with Toxorhynchites rutilis rutilis Coquillett, showed that this species had a high success rate in artificial breeding containers.  In a 12.6 hectare residential area, about 70% of the available oviposition sites were located over a 14-day period by two releases of 175 females.  Mass culturing techniques have been developed for this species and Toxorhynchites amboinensis (Doleschall) (Focks & Boston 1979, Riviere et al. 1987b).

 

Focks et al (1986), working with Toxorhynchites amboinensis, reported that release of 100 females per block for several weeks, combined with ultra low volume application of malathion, reduced Ae. aegypti populations by about 96% in a residential area of New Orleans.  The Toxorhynchites releases and not the insecticide treatment apparently accounted for most of the reduction.  These workers noted that reducing both the number of predators and malathion applications without lowering efficacy could further refine the procedure.  Mosquitoes such as Ae. aegypti and Ae. albopictus, which breed in and whose eggs are dispersed via artificial containers, pose major health hazards as vectors of human diseases throughout much of the warmer climates of the world.  The massive quantities of containerized products and rubber tires which are then discarded without care or stockpiled, have given these mosquito species a tremendous ecological advantage.  The recent establishment and extensive spread of Ae. albopictus in the United States underlines this point (Sprenger & Wuithironyagool 1986).  The apparent inability of governments to appropriately control disposal of these containers and difficulties in location once they are discarded makes inundative releases of Toxorhynchites, either alone or in combination with other control tactics, a much more plausible approach (Focks et al. 1986, Riviere et al. 1987a).

 

Notonectids are voracious predators of mosquito larvae under experimental conditions (Ellis & Borden 1970, Garcia et al. 1974, Hazelrig 1974), and in waterfowl refuges in California's Central Valley (Legner & Sjogren, unpub. data).  Notonecta undulata Say and Notonecta unifasciata Guerin have been colonized in the laboratory.  In addition, collection of large numbers of eggs, nymphs and adults is feasible from such breeding sites as sewage oxidation ponds (Ellis & Borden 1969, Garcia 1973, Hazelrig 1975, Sjogren & Legner 1974, Muira 1986).  Some studies have been conducted on storage of eggs at low temperatures, but viability decreased rapidly with time (Sjogren & Legner 1989).  At present, the most feasible use of these predators appears to lie in the recovery of eggs from wild populations on artificial oviposition materials and their redistribution to mosquito breeding sites.  Such investigations were carried out in central California rice fields by Miura (1986).  Floating vegetation such as algal mats and sometimes duck weed (Lemna spp.) form protective refugia for mosquito larvae, and consequently populations of mosquitoes can be high in the presence of notonectids (Garcia et al. 1974).  It appears that colonization and mass production costs, coupled with the logistics of distribution, handling and timing of release at the appropriate breeding site, are almost insurmountable problems for routine use of notonectids in mosquito control.

 

In addition to insect predators, several crustaceans feed on mosquito larvae.  Among these are the tadpole shrimp, Triops longicaudatus (LeConte), and several copepod species.  Mulla et al. (1986) and Tietze & Mulla (1987), investigating the tadpole shrimp, showed that it was an effective predator under laboratory conditions and speculated that it may play an important role in the field against flood water Aedes and Psorophora species in southern California.  Drought resistance in predator eggs is an appealing attribute for egg production, storage and manipulationin field situations against these mosquitoes.  However, synchrony in hatch and development between the predator and the prey is crucial if this is to be a successful biological control agent for the rapidly developing Aedes and Psorophora spp.  In addition, the tadpole shrimp is considered an important pest in commercial rice fields.

 

Miura & Takahashi (1985) reported that Cyclops vernalis Fisher was an effective predator on early instar Cx. tarsalis larvae in the laboratory.  These workers speculated that copepods could have an important role in suppressing mosquito populations in rice fields because of their feeding behavior and abundance.

 

Another crustacean that has shown promise for more extensive application is the cyclopoid predator, Mesocyclops aspericornis Daday (Riviere et al. 1987b).  This work has shown reductions of Ae. aegypti and Ae. polynesiensis Marks by more than 90% after inoculative release of the organism into artificial containers, wells, treeholes and land crab burrows.  Although not able to withstand desiccation, the rather small cyclopod predator has persisted almost 2.5 years in crabholes and up to five years in wells, tires and treeholes under subtropical conditions.  This species can be mass-produced, but its occurrence in large numbers in local water sources allows for the inexpensive and widespread application to mosquito breeding sites in Polynesia (Riviere et al. 1987a,b).  The species is also very tolerant of salinities greater than 50 parts per thousand.  The benthic feeding behavior of Mesocyclops makes it an effective predator of the bottom foraging Aedes, but limits effectiveness against surface foraging mosquitoes.  Riviere et al. (1987a,b) believed that the effectiveness against Aedes is due to a combination of predation and competition for food.  Perhaps the greatest utility of this Mesocyclops will lie in the control of crabhole breeding species, such as Ae. polynesiensis in the South Pacific.  Further investigations may uncover additional cyclopods that can impact other mosquito species.

 

The most important nonarthropod invertebrate predators to draw attention for mosquito control are the turbellarian flatworms and a coelenterate.  Several flatworm species have been shown to be excellent predators of mosquito larvae in a variety of aquatic habitats (Legner & Medved 1974, Yu & Legner 1976, Collins & Washino 1978, Case & Washino 1979, Legner 1977,  1979,  Ali & Mulla 1983, George et al. 1983).  Several biological and ecological attributes of flatworms would seem to make them ideal candidates for manipulative use.  Among them are ease of mass production, an overwintering embryo, effective predatory behavior in shallow waters with emergent vegetation, on site exponential reproduction following inoculation (Medved & Legner 1974, Tsai & Legner 1977, Legner & Tsai 1978, Legner 1979) and tolerance to environmental contaminants (Levy & Miller 1978, Nelson 1979). 

 

Collins & Washino (1978) and Case & Washino (1979) suggested that flatworms, particularly Mesostoma, may play an important role in the natural regulation of mosquitoes in some California rice fields because of their densities and their predatory attack on mosquito larvae in sentinel cages.  Preliminary analysis using extensive sampling showed a significant negative correlation between the presence of flatworms and population levels of Cx. tarsalis and An. freeborni (Case & Washino 1979).  However, these workers cautioned that an alternative hypothesis related to the ecology of these species may have accounted for the correlations.  Later investigations by Palchick & Washino (1984), employing more restrictive sampling, were not able to confirm the correlations between Mesostoma and mosquito populations.  However, the enormity of the problem associated with sampling in California rice fields, coupled with the complexity of the prey and predator interactions, make further studies necessary before the role of this group of flatworms in rice fields can be clearly established.

 

The important attributes for manipulative use of flatworms mentioned above raises the question of why they have not been developed further for use in mosquito control.  Perhaps the contemporary development of Bacillus thuringiensis var. israelensis DeBarjac (H-14), a highly selective easily applied microbial insecticide, may have been at least partially responsible for slowing further work and development of these predators.  Their mass culture must be continuous and demands skilled technical assistants (Legner & Tsai 1978).  Their persistence in field habitats may also depend on the presence of other organisms, such as ostracods, which can be utilized for food during low mosquito abundance (Legner et al. 1976).

 

The coelenterates, like the flatworms, showed great promise for further development and use in selected breeding habitats.  Chlorohydra viridissima (Pallas) is efficient in suppressing culicine larvae in ponds with dense vegetation and this species also can be mass produced (Lenhoff & Brown 1970, Yu et al. 1974a,b, 1975).  However, like the flatworms, work on these predators has waned, perhaps for similar reasons as speculated for the flatworms.  Microbial pesticides can be employed over an extensive range of different mosquito breeding habitats.  Also, commercial production of flatworms and coelenterates would be much more costly, and storage of viable cultures all but impossible.

 

Fungi.--The most promising fungal pathogen is a highly selective and environmentally safe oomycete, Lagenidium giganteum Couch. First tested for its pathogenicity to mosquitoes in the field by McCray et al. (1973), it is applied by aircraft to rice fields (Kerwin & Washino 1987).  Lagenidium develops asexually and sexually in mosquito larvae, and is capable of recycling in standing bodies of water.  This creates the potential for prolonged infection in overlapping generations of mosquitoes.  Lagenidium may also remain dormant after the water source has dried up and then become active again when water returns.  The sexually produced oospore offers the most promising stage for commercial production because of its resistance to desiccation and long-term stability.  However, problems in production and activation of the oospores still remain (Axtell et al. 1982, Merriam & Axtell 1982a,b, 1983; Jaronski & Axtell 1983a,b,c, Kerwin et al. 1986, Kerwin & Washino 1987).  Field trials with the sexual oospore and the asexual zoospore indicate that this mosquito pathogen is near the goal of practical utilization.  Kerwin et al (1986) reports that the asynchronous germination of the oospore is of particular advantage in breeding sources where larval populations of mosquitoes are relatively low, but recruitment of mosquitoes is continuous due to successive and overlapping generations, as in California rice fields.  The germination of oospores over several months provides long-term control for these continuous low level populations.  In addition, the asexual zoospores arising from the oospore infected mosquito is available every two to three days to respond in a density dependent manner to suppress any resurging mosquito population.  This stage survives about 48 hours after emerging from the infected host.

 

Kerwin et al. (1986) indicate that laboratory fermentation production of the asexual stage of Lagenidium for controlling mosquitoes in the field is approaching the development requirements and costs for the production of Bacillus thuringiensis israelensis.  A distinct advantage of this pathogen over the Bacillus is its potential to recycle through successive host generations.  The disadvantage of the asexual stage is that it is relatively fragile, cannot be dried and has a maximum storage life of only eight weeks (Kerwin & Washino 1987).  Thus, the focus of attention for commercial production is on the oospore, which is resistant to desiccation and can be easily stored.  Axtell & Guzman (1987) have recently encapsulated both the sexual and asexual stages in calcium alginate and reported activity against mosquito larvae after storage for up to 35 and 75 days, respectively.  Further refinement in techniques of production and encapsulation might make this approach a viable option for future commercial production and application.

 

Limitations on the use of this pathogen include intolerance to polluted water, salinity and other environmental factors (Jaronski & Axtell 1982, Lord & Roberts 1985, Kerwin & Washino 1987).  However, there are numerous mosquito breeding sources where these limitations do not exist and therefore one would expect to see this selective and persistent pathogen available for routine mosquito control in the near future.

 

The fungus Culicinomyces clavosporus Couch, Romney & Rao, first isolated from laboratory mosquito colonies and later from field habitats, has been under research and development for more than a decade (Sweeney et al. 1973, Couch et al. 1974, Russell et al. 1979, Frances et al. 1985).  The fungus is active against a wide range of mosquito species and also causes infections in other aquatic Diptera (Knight 1980, Sweeney 1981).  The ease of production with relatively inexpensive media in fermentation tanks is an extremely desirable trait.  However, problems in storage must be overcome if this fungus is to be widely used.  Perhaps a drying process, now being investigated, will solve storage requirements (Sweeney 1987).  Although the fungus has shown high infection rates in field trials, dosage rates have been high and appreciable persistence at the site has not been demonstrated (Sweeney et al. 1973, Lacey & Undeen 1986, Sweeney 1983, 1987).

 

Various species of Coelomomyces have been studied over the last two decades for use in mosquito control.  Natural epizootics with infection rates in excess of 90% have been recorded.  These fungi persist in certain habitats for long periods; however, factors triggering outbreaks in these situations are not well understood (Chapman 1974).  Some field-testing has been done, but results have been highly variable (Federici 1981).  In general, difficulties associated with the complex life cycle of these fungi have encumbered research on them.  Federici (1981) and Lacey & Undeen (1986) have reviewed the potential of these fungi for mosquito control.

 

Nematodes.--Among the various nematodes pathogenic for mosquitoes, Romanomermis culicivorax Ross & Smith, has received the most attention (Petersen & Willis 1970, 1972a,b, 1975; Brown et al. 1977, Brown & Platzer 1977, Poinar 1979, Petersen 1980a,b, Brown-Westerdahl et al. 1982, Kerwin & Washino 1984).  This mermithid, which is active against a wide range of mosquito species, has been mass produced (Petersen & Willis 1972a) and utilized in a number of field trials.  The nematode was commercially produced and sold under the name Skeeter Doom TMR, but according to Service (1983) eggs showed reduced viability in transport and the product currently is no longer sold.  However, the nematode's ability to recycle through multigenerations of mosquitoes and overwinter in various habitats, including drained, harvested, stubble-burned, cultivated and replanted rice fields, are strong attributes favoring its further research and development for biological control (Petersen & Willis 1975, Brown-Westerdahl et al. 1982).  Several field applications have shown good results and have included both the preparasitic stage and post parasitic stages with the former more applicable to the "quick kill" and the latter for more long-term continuous control such as in California rice fields (Petersen et al. 1978a,b, Levy et al. 1979, Brown-Westerdahl et al. 1982).  Some drawbacks to its widespread use include intolerance to low levels of salinity, polluted water and low oxygen levels, predation by aquatic organisms and the potential for development of resistance by the host (Petersen & Willis 1970, Brown & Platzer 1977, Brown et al. 1977, Petersen 1978, Brown-Westerdahl 1982).  However, these environmental problems are not generally an issue for anopheline control.  For control of these species the cost of in vivo mass production clearly stands as the major drawback for this pathogen.  Perhaps its most plausible use will be in specialized habitats integrated with other control strategies (Brown-Westerdahl et al. 1982).

 

Bacteria.--The spore forming bacterial pathogen, Bacillus thuringiensis var. israelensis (H-14), was isolated by Goldberg & Margalit (1977) and the produced toxin has been shown by numerous studies to be an effective and environmentally sound microbial insecticide against mosquitoes and blackflies.  Its high degree of specificity and toxicity, coupled with its relative ease of production, has made it the most widely used microbial product to date for mosquito and blackfly control.  Several formulations are currently available from commercial firms throughout the world.  Their efficacies under different environmental conditions and problems associated with its use have been reviewed by Garcia (1986, 1987) and Lacey & Undeen (1986).

 

Another spore forming bacterium, Bacillus sphaericus Neide, has also shown great promise as a larvacide against certain mosquito species (Mulla et al. 1984).  In general, several strains of this pathogen show a much higher degree of toxic variability among species of mosquitoes.  Culex spp. appear to be highly susceptible, whereas other species such as Ae. aegypti are highly refractory.  Unlike the ephemeral larvacidal activity of Bacillus t. i. toxin, some strains of B. sphaericus have shown persistence and apparent recycling in certain aquatic habitats (DesRochers & Garcia 1984).  For further detail see the recent review by Lacey & Undeen (1986).

 

Protozoa.--A large number of protozoa have been isolated from mosquitoes and other medically important arthropods (Roberts et al. 1983, Lacey & Undeen 1986).  Of this assemblage the microsporidians have been studied rather intensively.  Due to their complex life cycle and the in vivo production methods necessary for maintaining them, research on their practical utility has been limited.  However, as Lacey & Undeen (1986) point out, if more information is developed on their life cycle, it may be found that they could play a role in suppressing mosquitoes through inoculative and augmentive releases in certain habitats.

 

Among the other protozoa that show promise is the endoparasitic ciliate, Lambornella clarki Corliss & Coats, a natural pathogen of the treehole mosquito, Aedes sierrensis Ludlow.  This pathogen has received considerable attention over the last few years as a potential biological control agent for container breeding mosquitoes (Egeter et al. 1986, Washburn & Anderson 1986).  Desiccation resistant cysts allow persistence of the ciliate from one year to the next.  Currently, in vitro production methods are being developed and small field trials are being initiated to determine its efficacy and practicability for field use (Anderson et al. 1986a,b).

 

Viruses.--Numerous pathogenic viruses have been isolated from mosquitoes and blackflies.  However, to date none look promising for practical use in control (Lacey & Undeen 1986).

 

For further detail on biological mosquito control please refer to Reviews.

 

 

REFERENCES:  [Detailed = <medvet.ref.htm> ]  [Additional references may be found at:   MELVYL Library ]

 

 

Ali, A. & M. S. Mulla.  1983.  Evaluation of the planarian, Dugesia dorotocephala, as a predator of chironomid midges and mosquitoes in experimental ponds.  Mosquito News 43:  46-49.

 

Axtell, R. C., S. T. Jaronski & T. L. Merriam.  1982.  Efficacy of the mosquito fungal pathogen, Lagenidium giganteum (Oomycetes: Lagenidiales).  Proc. Calif. Mosq. Vector Control Assoc. 50:  41-2.

 

Case, T. J. & R. K. Washino.  1979.  Flatworm control of mosquito larvae in rice fields.  Science 206:  1412-14.

 

Christensen, J. B., J. L. Fetter-Lasko, R. K. Washino, R. C. Husbands & E. E. Kaufman.  1977.  A preliminary field study employing Lagenidium giganteum, a fungus, as a possible biological control agent against the pasture mosquito Aedes nigromaculis.  Proc. Calif. Mosq. Vector Control Assoc. 45:  105.

 

Collins, F. H. & R. K. Washino.  1978.  Microturbellarians as natural predators of mosquito larvae in northern California rice fields.  Proc. Calif. Mosq. Vect. Contr. Assoc. 46:  91.

 

Collins, F. H. & R. K. Washino.  1979.  Factors affecting the density of Culex tarsalis and Anopheles freeborni in northern California rice fields.  Proc. Calif. Mosq. Control Assoc. 47:  97-98.

 

Domnas, A. J., S. M. Fagan & S. T. Jaronski.  1982.  Factors influencing zoospore production in liquid cultures of the mosquito pathogen Lagenidium giganteum (Oomycetes:  Lagenidiales).  Mycologia 75:  820-25.

 

1999   Garcia. R. & Legner, E. F..  1999.  The biological control of medical and veterinary pests. In:  Fisher, T. W. & T. S. Bellows, Jr. (eds)  Handbook of Biological Control:  Principles and Applications.  Academic Press, San Diego, CA. 1046 p.

 

George, J. A.  1978.  The potential of a local planarian, Dugesia tigrina (Tricladida, Turbellaria), for the control of mosquitoes in Ontario.  Proc. Ent. Soc. Ont. 109:  65-9.

 

George, J. A., B. A. L. Nagy & J. W. Stewart.  1983.  Efficacy of Dugesia tigrina (Tricladida: Turbellaria) in reducing Culex numbers in both field and laboratory.  Mosq. News 43:  281-87.

 

Glenn, F. E. & H. E. Chapman.  1978.  A natural epizootic of the aquatic fungus Lagenidium giganteum in the mosquito Culex territans.  Mosq. News 38:  522-24.

 

158.   Hauser, W. J., E. F. Legner, R. A. Medved & S. Platt.  1976.  Tilapia-- a management tool for biological control of aquatic weeds and

           insects.  Bull. Amer. Fisheries Soc. 1(2):  15-16.

 

160.   Hauser, W. J. & E. F. Legner.  1976.  Simple, inexpensive technique for tagging fish.  The Progressive Fish Culturist 38(1):  18-19.

 

168.   Hauser, W. J., E. F. Legner & F. E. Robinson.  1977.  Biological control of aquatic weeds by fish in irrigation channels.  Proc. Water

           Management For Irrigation & Drainage.  ASCE/Reno, Nevada, Jul. 20-22.  pp. 139-145.

 

Jaronski, S. T. & R. C. Axtell.  1982.  Effects of organic water pollution on the infectivity of the fungus Lagenidium giganteum (Oomycetes; Lagenidiales) for mosquito larvae (Culex quinquefasciatus): Field and laboratory evaluation.  J. Med. Ent. 19:  255-62.

 

Jaronski, S. T. & R. C. Axtell.  1983a.  Effects of temperature on infection growth and zoosporogenesis of Lagenidium giganteum, a fungal pathogen of mosquito larvae.  Mosq. News 43:  42-5.

 

Jaronski, S. T. & R. C. Axtell.  1983b.  Persistence of the mosquito fungal pathogen Lagenidium giganteum (Oomycetes; Lagenidiales) after introduction into natural habitats.  Mosquito News 43:  332-37.

 

Jaronski, S. T., R. C. Axtell, S. M. Fagan & A. J. Domnas.  1983.  In vitro production of zoospores by the mosquito pathogen Lagenidium giganteum (Oomycetes: Lagenidiales) on solid media.  J. Invert. Path. 41:  305-09.

 

Kenk, R.  1972.  Freshwater planarians (Turbellaria) of North America.  Biota of freshwater ecosystems identification Manual No. 1, Smithsonian Institution, Washington, D. C.  81 p.

 

Lamborn, R. H.  1890.  Dragon Flies vs. Mosquitoes.  D. Appleton Co., New York.  202 p.

 

Legner, E. F. 1977.  Response of Culex spp. larvae and their natural insect predators to two inoculation rates with Dugesia dorotocephala (Woodworth) in shallow ponds.  Mosq. News 37:  435-40.

 

1984  Legner, E. F. & R. D. Sjogren.  1984.  Biological mosquito control furthered by advances in technology and research.  J. Amer. Mosq.

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1974  Legner, E. F., R. D. Sjogren & I. M. Hall.  1974.  The biological control of medically important arthropods.  Critical Reviews in

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1975  Legner, E. F., R. A. Medved & W. J. Hauser.  1975.  Predation by the desert pupfish, Cyprinodon macularius on Culex mosquitoes and

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1978a   Legner, E. F.  1978a.  Efforts to control Hydrilla verticillata Royle with herbivorous Tilapia zillii (Gervais) in Imperial County irrigation

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1978b  Legner, E. F.  1978b.  Mass culture of Tilapia zillii [Cichlidae] in pond ecosystems.  Entomophaga 23(1):  51-56.

 

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1973  Legner, E. F. & R. A. Medved.  1973.  Influence of Tilapia mossambica (Peters), T. zillii (Gervais) (Cichlidae) and Mollienesia latipinna

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1974  Legner, E. F. & R. A. Medved.  1974.  Laboratory and small-scale field experiments with planaria (Tricladida, Turbellaria) as biological

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1978  Legner, E. F. & S.-C. Tsai.  1978.  Increasing fission rate of the planarian mosquito predator, Dugesia dorotocephala, through biological

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1990  Legner, E. F. & R. W. Warkentin.  1990.  Rationale for the desert pupfish, Cyprinodon macularius, as a complement to Gambusia in

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1976  Legner, E. F., T.-C. Tsai & R. A. Medved.  1976.  Environmental stimulants to asexual reproduction in the planarian, Dugesia

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Lenhoff, M. H. & R. D. Brown.  1970.  Mass culture of hydra:  improved method and application to other invertebrates.  Lab. Anim. 4:  139-54.

 

Levy, R. & T. W. Miller, Jr.  1978.  Tolerance of the planarian Dugesia dorotocephala to high concentrations of pesticides and growth regulators.  Entomophaga 23:  31-34.

 

McCray, E. M., D. J. Womeldorf, R. C. Husbands and D. A. Eliason.  1973.  Laboratory observations and field tests with Lagenidium against California mosquitoes.  Proc. Calif. Mosq. Control Assoc. 41:  123-28.

 

Medved, R. A. & E. F. Legner.  1974.  Feeding and reproduction of the planarian, Dugesia dorotocephala (Woodworth), in the presence of Culex peus Speiser.  Environ. Ent. 3:  637-41.

 

Meyer, H. J. & L. W. Learned.  1981a.  Laboratory studies on the potential of Dugesia tigrina for mosquito predation.  Mosq. News 41:  760-64.

 

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Nelson, F. R. S.  1979.  Comparative predatory potential and asexual reproduction of sectioned Dugesia dorotocephala as they relate to biological control of mosquito vectors.  Environ. Ent. 8:  679-81.

 

Palchick, S. & R. K. Washino.  1984.  Factors affecting mosquito larval abundance in northern California rice fields.  Proc. Calif. Mosq. Control Assoc. 52:  144-47.

 

Service, M. W.  1983.  Biological control of mosquitoes--has it a future?  Mosq. News 43:  113-20.

 

1977   Tsai, S.-C. & E. F. Legner.  1977.  Exponential growth in culture of the planarian mosquito predator, Dugesia dorotocephala

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1980  Walters, L. L. & E. F. Legner.  1980.  Impact of the desert pupfish, Cyprinodon macularius, and Gambusia affinis on fauna in pond

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Washino, R. K.  1981.  Biocontrol of mosquitoes associated with California rice fields with special reference to the recycling of Lagenidium giganteum Couch and other microbial agents. p. 122-39. In:  M. Laird (ed.), Biocontrol of Medical and Veterinary Pests.  Praeger Publ., New York. 

 

Washino, R. K. & C. K. Fukushima.  1978.  Assessment of biological control agents against mosquito larvae in Northern California: A progress report.  Proc. Calif. Mosq. Vector Control Assoc. 46:  89.

 

Yu, H.-S. & E. F. Legner.  1976.  regulation of aquatic Diptera by planaria.  Entomophaga 21: 31-12.

 

Yu, H.-S., E. F. Legner & R. D. Sjogren.  1974a.  Mosquito control with European green hydra in irrigated pastures, river seepage and duck club ponds in Kern County.  Proc. Calif. Mosq. Contr. Assoc. 42:  77-78.

 

Yu, H.-S., E. F. Legner & R. D. Sjogren.  1974b.  Mass release effects of Chlorohydra viridissima (Coelenterata) on field populations of Aedes nigromaculis and Culex tarsalis in Kern County, California.  Entomophaga 19:  409-20.

 

Yu, H.-S., E. F. Legner & F. Pelsue.  1975.  Control of Culex mosquitoes in weedy lake habitats in Los Angeles with Chlorohydra viridissima.  Proc. Calif. Mosq. Contr. Assoc. 43:  123-26.