Chapter 14. Biting Flies
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389 Chapter 14 Biting Flies (Culicidae, Ceratopogonidae, Tabanidae) of the Prairies Ecozone Timothy J. Lysyk Agriculture and Agri-Food Canada Research Station Lethbridge, Alberta, Canada, T1J 4B1 Terry D. Galloway Department of Entomology, University of Manitoba Winnipeg, Manitoba, Canada, R3T 2N2 Abstract. This chapter lists 81 species of biting fl ies from the families Culicidae, Ceratopogonidae (genus Culicoides), and Tabanidae for the Canadian Prairies. Twenty-fi ve species of Culicidae are listed, including one species of Anophelinae and 25 species of Culicinae. Twenty-six species of Culicoides are listed. This group has been the least intensively studied in Canadian grasslands, and this is undoubtedly an underestimate of the number of species present. Thirty species of Tabanidae are listed, including seven species of Chrysopsinae and 23 species of Tabaninae. All three families are readily captured using a variety of trapping methods. Identifi cation of the Culicidae and Tabanidae is facilitated by the availability of excellent identifi cation resources. Identifi cation of the genus Culicoides is hampered by the lack of a unifi ed key for western Canada. Despite this, there are many opportunities for investigators to increase knowledge of these groups in Canadian grasslands. Résumé. Ce chapitre présente une liste des 81 espèces de mouches piqueuses appartenent aux familles des culicidés, des cératopogonidés (genre Culicoides) et des tabanidés présentes dans les prairies canadiennes. Cette liste renferme 25 espèces de culicidés, y compris une espèce de la sous-famille des anophélinés et 25 espèces de la sous-famille des culicinés, ainsi que 26 espèces du genre Culicoides. Ces diptères forment le groupe le moins étudié des prairies canadiennes, et la liste proposée sous-estime donc sans doute le nombre réel d’espèces présentes dans cette région. La liste compte 30 espèces de tabanidés, y compris sept espèces de chrysopsinés et 23 espèces de tabaninés. Tous ces insectes sont faciles à recenser à l’aide de diverses méthodes de capture. Les ressources documentaires disponibles facilitent l’identifi cation des culicidés et des tabanidés. Par contre, l’identifi cation des espèces du genre Culicoides est compliquée par l’absence d’une clé unifi ée pour l’ouest du Canada. Malgré tout, les chercheurs jouissent de nombreuses occasions pour approfondir leur connaissance des diptères appartenant à ces groupes dans les prairies canadiennes. Introduction Biting fl ies are notorious for their impact on human health and welfare, and on the fi tness and performance of domestic animals and wildlife. Canada is renowned for its diversity of species of biting fl ies, representing four families and including mosquitoes, no-see-ums, black fl ies, horse fl ies, and deer fl ies. All species of these families in Canada rely upon the availability of aquatic habitats for their success. Although grasslands are better known for their terrestrial ecosystems, there is considerable variety in aquatic habitats interspersed throughout the Prairies Ecozone (Shorthouse 2010; Wrubleski and Ross 2011), which are essential components for most of these biting fl ies. Many species have very specifi c Lysyk, T. J. and T. D. Galloway. 2014. Biting Flies (Culicidae, Ceratopogonidae, Tabanidae) of the Prairies Ecozone. In Arthropods of Canadian Grasslands (Volume 3): Biodiversity and Systematics Part 1. Edited by H. A. Cárcamo and D. J. Giberson. Biological Survey of Canada. pp. 389-398. © 2014 Biological Survey of Canada. ISBN 978-0-9689321-6-2 doi: http://dx.doi.org/10.3752/9780968932162.ch14 390 T. J. Lysyk and T. D. Galloway habitat requirements. Black fl y larvae and pupae are found only in running water and, although they are an important element in many areas of grasslands in Canada, they are considered elsewhere in this volume (see Chapter 13). We focus on mosquitoes (Culicidae), no-see-ums (Ceratopogonidae), deer fl ies, and horse fl ies (Tabanidae) known to inhabit aquatic or moist organic habitats in prairie grasslands in Alberta, Saskatchewan, and Manitoba. Mosquito larvae and pupae are specialists found only in standing water, often in temporary aquatic habitats (Wood et al. 1979). Larvae of no-see-ums (Culicoides spp.) inhabit a wide variety of wetland or moist organic habitats (Kettle 1977). Most species of deer fl ies and horse fl ies in prairie grasslands inhabit permanent and semi-permanent wetlands, but some are found in running water (Teskey 1990). Given the impact of these biting fl ies on livestock production as a nuisance and as vectors of disease-causing agents, it is surprising that so little attention has been paid to them on the Prairies. Our objective is to highlight biting fl y species that inhabit the Canadian prairie grasslands and to identify gaps in our knowledge about these groups. Criteria for Inclusion We have chosen to include those species of Culicidae, Ceratopogonidae, and Tabanidae that are known to reproduce and are established in the Canadian prairie grassland regions of Alberta, Saskatchewan, and Manitoba (region identifi ed in Shorthouse and Larson 2010). Some species are restricted to these grassland regions, while others are habitat generalists and have extensive ranges that happen to include prairie grasslands. Some species of biting fl ies might have considerable dispersal capacity, carried on strong southerly winds, for example, from distant locations. Unless there is evidence that a species is a permanent resident of our selected study area, it is not included here. Family Culicidae Species records were extracted from a variety of published sources, including Rempel (1950, 1953), Wood et al. (1979), and regional studies of mosquitoes associated with particular grassland habitats (Shemanchuk 1959, 1969; Shemanchuk et al. 1963; Scholefi eld et al. 1981; Lysyk 2010). Three subfamilies are represented in the Culicidae, of which two, the Anophelinae and Culicinae, occur in the Prairie region. Anopheles earlei is the only representative of the Anophelinae that occurs in the Prairies Ecozone. This species is widespread but relatively rare in grasslands (Rempel 1950). Adult females overwinter in subterranean environments such as mammal burrows (Shemanchuk 1965). Adults emerge from burrows in the spring and lay eggs singly on standing water (Anderson and Gallaway 1988). The subfamily Culicinae has three tribes with representatives in Canadian grasslands. The tribe Culicini is represented by one species, Culex tarsalis. This species also overwinters as adult females in mammalian burrows (Shemanchuk 1965) and lays eggs in rafts on grassy pools of permanent and semi-permanent standing water. Culex tarsalis is common in grasslands and feeds readily on birds, large mammals, and humans. It is the principal vector of Western equine encephalitis virus (Shemanchuk and Morgante 1968) and West Nile virus (Turell et al. 2005) in western North America. The tribe Culisetini includes two representatives in the Canadian grasslands. Culiseta alaskaensis has been reported in grasslands (Strickland 1938; Shemanchuk 1959; Lysyk 2010) but is relatively uncommon; this species tends to be more abundant farther north. Culiseta inornata is widely distributed Biting Flies (Culicidae, Ceratopogonidae, Tabanidae) of the Prairies Ecozone 391 and may be among the most abundant mosquito species near areas inhabited by livestock (Lysyk 2010). It feeds preferentially on large mammals such as cattle and horses, and has been implicated as a vector of a variety of pathogens (Shemanchuk and Morgante 1968). Both of these Culiseta species also overwinter as adults and lay eggs as rafts on the surface of standing water. Larvae of Cs. inornata do best at lower temperatures (Brust and Hanec 1967), and egg rafts are more often laid in shaded pools. The tribe Aedini in the prairie grasslands, represented by the genera Ochlerotatus, Aedes, Coquillettidia, and Psorophora, includes at least 21 species, most of which oviposit on the soil and organic matter on the margins of temporary aquatic habitats (except Coquillettidia; see below). The eggs are the overwintering stage and hatch under suitable conditions when submerged by snowmelt or summer fl ood water (Dixon and Brust 1972). Most of these species are univoltine, their only generation developing in snowmelt pools in the spring, while some (e.g., Oc. spencerii, Oc. sticticus, Ae. cinereus) produce batches of mixed diapausing and non-diapausing eggs (Brust 1968), or are multivoltine (e.g., Oc. campestris, Oc. dorsalis, Oc. melanimon, Ae. vexans) (Tauthong and Brust 1977; Wood et al. 1979). Aedes vexans is a multivoltine fl ood-water species, which, under ideal conditions, can produce many generations in a summer, emerging in extraordinary numbers and causing severe stress to humans and other animals. These Ochlerotatus and Aedes species are well adapted to grassland habitats where drought is a common phenomenon; their eggs may lay dormant for many years in the absence of suffi cient snowmelt water or rainfall (e.g., Gjullin et al. 1950). The most common aedine species in grasslands are Ae. vexans, Oc. dorsalis, Oc. campestris, Oc. melanimon, Oc. spencerii, Oc. fl avescens, and Oc. nigromaculis (Shemanchuk 1959; Lysyk 2010). Ochlerotatus sticticus occurs sporadically on the Prairies but can be abundant. It oviposits in wooded areas along the fl ood plains near large rivers (Trpis et al. 1973) and occurs in large numbers during years of heavy rainfall (Lysyk 2010). The remaining 11 species occur sporadically in grassland areas; they live more typically on the periphery of true grassland habitats, being considered primarily woodland, parkland, or northern species. Some are rarely collected species throughout their range and their status in grasslands remains to be confi rmed. Ochlerotatus euedes and Oc. implicatus are widespread (Scholefi eld et al. 1981), but were not detected in recent surveys in grasslands in Alberta (Lysyk 2010). Ochlerotatus fi tchii, Oc. increpitus, and Oc. cataphylla were considered ubiquitous in southern Alberta by Scholefi eld et al. (1981), but as woodland species by Rempel (1950). Ochlerotatus cataphylla was collected in grasslands by Shemanchuk (1959, 1969) and Lysyk (2010), although in low numbers.