Article

Arthropods of Canadian grasslands: a retrospective of a 40-year project of the Biological Survey of Canada

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  • Agriculture and Agri-Food Canada, Lethbridge, Canada
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Abstract

The Biological Survey of Canada initiated a project in 1979 to collect and synthesise information on the native arthropod fauna of the vanishing grassland habitats of Canada. At that time, it was thought that the Canadian arthropod fauna might comprise about 66 000 species. Recent studies suggest that the fauna may exceed 100 000 species, of which >25% may occur in the Prairies Ecozone. Results of this near 40-year project have been published in four volumes of the Arthropods of Canadian Grasslands monograph series of the Biological Survey of Canada. Here, the editors of this series review the grasslands project of the Biological Survey of Canada, summarise the contents of the volumes, and discuss current knowledge on the diversity of the grasslands arthropods of Canada. Whereas information on the species richness of some groups in the Prairies Ecozone is largely complete, information on the diversity of many other groups remains sparse. Reviewing the steps between initiation and publication of the Arthropods of Canadian Grasslands series may aid development of similar projects elsewhere. Identifying knowledge gaps will direct future research efforts. Identifying the diversity of grassland arthropods, their distribution and abundance, and the ecosystem services that they provide will facilitate efforts to conserve the remaining grassland habitats in Canada.

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... Therefore, the history of the BSC is also, to some extent, a history of arthropod faunistic studies in Canada. Floate et al. (2017) illustrate this in their retrospective paper on the BSC's long-running "Arthropods of Canadian Grasslands" project. They trace the project from the original choice of grassland ecosystems for study due to rapid habitat loss and lack of faunal information, through a multi-year process of identifying needs and gaps, to its milestone achievement of publishing a four-volume series summarising current knowledge on the geography, climate, ecology, and biodiversity of these fragile ecoregions. ...
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The Biological Survey of Canada turns 40: a special issue for a special occasion - Volume 149 Issue 6 - Donna J. Giberson, Héctor A. Cárcamo
... Biodiversity studies conducted in agroecosystems of the Canadian Prairies focus primarily on carabid beetles (Coleoptera: Carabidae) ( Holliday et al. 2014), although some information on other taxa, such as ants (Hymenoptera: Formicidae) is available. The Biological Survey of Canada has been instrumental in advancing our knowledge of Prairies Ecozone arthropods ( Floate et al. 2017). One of its volumes is largely devoted to prairie agroecosystems (Floate 2011). ...
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This chapter describes the insect fauna of Ojibway Prairie, a tallgrass prairie complex in southern Ontario, highlighting the tallgrass-dependent and tallgrass-associated species among the over 2,000 insect species found there so far. The presence of tallgrass-dependent and tallgrass-associated species reflects Ojibway Prairie's status as a fragment of a formerly more continuous grassland and thus supports the prairie peninsula hypothesis. The chapter includes a discussion of insect species associated with other southern Ontario tallgrass prairie sites and compares these species with those found in Ojibway Prairie. Also discussed are rare species found at Ojibway Prairie but not associated specifically with tallgrass habitats. Forty-four insect species new to Canada or new to Ontario (1 Orthoptera, 3 Hemiptera, 10 Coleoptera, 16 Diptera, and 14 Hymenoptera) are recorded from Ojibway Prairie. Résumé. Ce chapitre décrit l'entomofaune de la prairie Ojibway, un complexe de prairies à herbes hautes du sud de l'Ontario, en portant une attention particulière aux espèces dépendantes des herbes hautes ou associées à ces dernières et qui sont au nombre des quelque 2 000 espèces d'insectes recensées jusqu'ici à cet endroit. La présence d'insectes dépendants des herbes hautes ou associés à ces dernières est un reflet de l'état actuel de la prairie Ojibway, qui n'est plus qu'un fragment d'une prairie autrefois plus continue, et vient appuyer l'hypothèse de la « péninsule de prairie ». Le chapitre traite également des espèces d'insectes associées à d'autres prairies à herbes hautes du sud de l'Ontario et compare ces espèces à celles qui se trouvent dans la prairie Ojibway. Il examine enfin les espèces rares qui vivent dans cette prairie mais qui ne sont pas associées directement aux habitats d'herbes hautes. On a établi la présence dans la prairie Ojibway de 44 espèces nouvelles pour le Canada ou l'Ontario (1 orthoptère, 3 hémiptères, 10 coléoptères, 16 diptères et 14 hyménoptères).
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KEY FINDINGS Biodiversity – the variety of species and ecosystems and the ecological processes of which they are a part – has a paramount influence on Canada’s natural capital and its ability to deliver services. Those services, in turn, contribute to human health and well-being and support a wide range of economic sectors. Climate change, interacting with other human stressors such as pollution and landscape fragmentation, is already impacting biodiversity in Canada. Future impacts will be affected by the magnitude of continuing climate change and adaptation decisions made to enhance ecosystem resilience. Key findings of this chapter include: • Climate-related shifts in species distributions have already been documented in Canada. Future range shifts will include expansion, contraction and fragmentation in species-specific patterns. In many locations, differential range shifts among species are likely to result in novel ecosystems. • Phenological mismatches occur when shifts in the timing of life cycle events differ between dependent species and, as an example, can result in migrating species arriving at a site after the peak prey availability has passed. Phenological mismatches are expected to become more frequent in the future, as is hybridization. The impacts of hybridization can drive rare species to extinction or, in other cases, increase the adaptability of some species by introducing genetic variation. • For many species, the current and projected rates of environmental change are likely to exceed their natural ability to adapt, increasing stress and threatening biodiversity. As a result, climate change is magnifying the importance of managing ecosystems in a manner that enhances resilience and preserves biodiversity. • Protected areas, including parks, wildlife reserves and marine protected areas will play an important role in the conservation of biodiversity in a period of rapid change. Many protected areas will provide “refuge” or migration corridors for native species, serving to maintain genetic diversity. Protected areas tend to be more resilient than the intervening landscapes and waterscapes because they contain relatively intact ecosystems and are less impacted by non-climate stressors such as habitat loss and fragmentation. • Many Canadian jurisdictions are expanding their system of parks and other protected areas as part of their overall management plans and climate change adaptation strategies. Initiatives aimed at maintaining or restoring landscape connectivity serve to increase ecosystem resilience by enhancing the capacity for species to adjust their distribution in response to climate change. Associated research, monitoring, citizen science, public awareness, and visitor experience programs build understanding and help to engage the public in meaningful participatory decision-making. • The conservation community recognizes the value of ecological restoration in strengthening the resilience of ecosystems to climate change. Integration of climate change adaptation strategies into restoration decision-making in Canada, as elsewhere, is complex.
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With more than 19,000 described species worldwide, parasitic wasps in the family Braconidae are the second largest group of Hymenoptera next to its sister lineage, Ichneumonidae. Despite their abundance and economic importance as potential biological control agents of forest and agricultural pests, little is known about the biodiversity of braconids in the Prairies Ecozone of Canada. The checklist of Braconidae was compiled by cross-referencing specimen localities with published records of braconid species found in the Prairie Provinces and supplemented with databased specimens from the Wallis-Roughley Museum of Entomology at the University of Manitoba. This checklist consists of 251 species, representing 22 different subfamilies, and includes14 new species records. Braconids in subfamilies such as Microgastrinae, Agathidinae, and Aphidiinae have a relatively large number of known species because of past research attention. Other subfamilies with fewer known species are undoubtedly more speciose than currently known, but are more difficult to identify because of a lack of taxonomic research and resources. It is hoped that this checklist serves as a baseline that will facilitate future biodiversity studies, conservation programs, and biological control research on Braconidae in the Prairies Ecozone of Canada.
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The Prairies Ecozone of southern Manitoba, Saskatchewan, and Alberta supports a diverse fauna, with 2,232 species of butterflies and moths (order Lepidoptera) recorded to date in 61 families. By far the best known Lepidoptera are the butterflies, with 177 species known to occur in the ecozone. The species known to occur in the Prairies Ecozone are listed by province. The Lepidoptera fauna of this ecozone is reviewed in terms of diversity, state of knowledge of the major groups, postglacial and relict patterns, recent changes in distribution, and endangered and threatened species.
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The prairie grasslands of Canada are home to at least 387 bee species. This represents almost half (i.e., 48%) of the bee taxa reported for Canada and over 90% of the total recorded from the three Prairie Provinces of Alberta, Saskatchewan, and Manitoba. The Prairies Ecozone thus represents one of the most diverse and important areas supporting bee diversity in the country, with 23% of the bee species listed not found anywhere else in Canada, a value similar to that of the tallgrass savanna of the Mixedwood Plains Ecozone (southern Ontario and Québec) and only surpassed by that of the bunchgrass/sagebrush grasslands of the Western Interior Basin Ecozone (south central British Columbia) with respect to endemism. However, the Canadian Prairies support a higher proportion of bee species with dietary specialization; over half of these are oligoleges of the Asteraceae. Over 70% of the native prairie grasslands were lost before 1990. Therefore, it is likely that many of the endemic floral specialists have also become much less common, though little baseline data exist for rigorous comparison. Much of the Canadian Prairies have not been surveyed extensively for bees, and several new records are reported here. A full taxonomic review of the bees of the prairie grasslands is presented, including bionomic summaries.
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Most Plecoptera (stonefl y) species require cool, well-oxygenated water and are therefore not as well represented in prairie grassland habitats as they are in steep mountain streams or forested habitats. One hundred thirty-one species of Plecoptera have been recorded from the Prairie Provinces of Alberta, Saskatchewan, and Manitoba, including 61 that occur in or border aquatic habitats in the Prairies Ecozone. Alberta has the highest stonefl y diversity because of its proximity to the mountains (108 species, 104 of which occur in the mountains), and the diversity in Saskatchewan is similar to that of Manitoba at 44 and 46 species, respectively. Only 2 of the 61 Prairies Ecozone species (Perlesta dakota and Pteronarcys pictetii) are restricted to this ecozone in Canada, and most of the species that occur in the Prairies Ecozone also occur in the Boreal Shield and Boreal Plains ecozones (40 species) and/or in the Montane Cordillera Ecozone (42 species). A list of species collected for each province and ecozone is provided, with references and probable refugial origins. Information on stonefl y ecology, taxonomic works, zoogeography, and importance as monitoring tools pertinent to the region is also presented. Résumé. La plupart des espèces de plécoptères (perles) ont besoin d'eau fraîche et bien oxygénée et ne sont donc pas aussi présentes dans les habitats des prairies qu'elles ne le sont dans les cours d'eau des habitats de montagne ou de forêt. On a recensé 131 espèces de plécoptères dans les provinces des prairies — Alberta, Saskatchewan et Manitoba —, y compris 61 vivant à l'intérieur ou à la périphérie d'habitats aquatiques de l'écozone des prairies. L'Alberta présente la plus grande diversité de plécoptères à cause de la proximité des Rocheuses (108 espèces, dont 104 se trouvent en montagne), tandis que la Saskatchewan et le Manitoba présentent des diversités semblables (44 et 46 espèces respectivement). Seules 2 des 61 espèces de l'écozone des prairies (Perlesta dakota et Pteronarcys pictetii) sont exclusives à cette écozone au Canada, la plupart des espèces observées dans l'écozone des prairies se trouvant également dans les écozones du bouclier boréal et des plaines boréales (40 espèces) ou dans l'écozone de la cordillère alpestre (42 espèces). Une liste des espèces prélevées dans chaque province et dans chaque écozone est fournie, accompagnée de références et d'informations sur les refuges d'où elles sont probablement issues. On présente enfi n des informations sur l'écologie des plécoptères, les études taxonomiques réalisées sur ces insectes, leur zoogéographie et leur importance en tant qu'outils de surveillance pertinents pour la région. Introduction Stonefl ies (Plecoptera) (Fig. 1) spend most of their life cycles as aquatic larvae before emerging from the water as terrestrial adults. The majority of stonefl ies require well-oxygenated water and are found in clean, cool, fast-fl owing streams and rivers (Hynes 1976; Stewart and Harper 1996; Stewart and Stark 2002, 2008), although a few species are also known from cold boreal and alpine lakes (Harper 1979; Donald and Anderson 1980; Dosdall and Lehmkuhl 1987). This restricts most Canadian species to areas such as the
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Canada's grasslands are located primarily in western Canada within the prairie provinces, but also with significant portions in the interior of British Columbia. Before European contact, their character and distribution were significantly influenced by disturbances from fire and large herbivores, which killed woody plants and produced a more arid environment where grasses were competitive. Aboriginal Indians also influenced these processes, both directly by increasing the number of fires either by accident or for strategic reasons (Lewis 1982) and indirectly through over-hunting (Kay 1994). Anthropogenic impacts were, therefore, present before European contact; whether or not these disturbances could be considered as natural is debatable. However, there is no question that the disturbances introduced through Eurocentric farming practices by settlers beginning early in the 19 th century and overtaken within the last 50 years by resource extraction economies were ecologically catastrophic. As a result, most of the grasslands have been cultivated and those that remain have been altered by grazing or severely fragmented by roads, conduits for energy, or urbanization. This chapter deals primarily with anthropogenic changes to the grasslands made since the arrival and establishment of Europeans. Résumé. Les prairies canadiennes se trouvent principalement dans l'ouest du Canada, dans les provinces des Prairies, mais il en existe également des portions importantes à l'intérieur de la Colombie-Britannique. Avant l'arrivée des Européens, leurs caractéristiques et leur répartition étaient en grande partie définies par l'action du feu et des grands herbivores qui détruisaient les plantes ligneuses et créaient un environnement plus aride, où les herbacées détenaient un avantage concurrentiel. Les autochtones influaient également sur ces processus, soit directement en augmentant le nombre d'incendies — par accident ou pour des raisons stratégiques (Lewis, 1982) —, soit indirectement par une chasse excessive (Kay, 1994). Les incidences anthropiques étaient donc déjà présentes avant l'arrivée des Européens, et la question de savoir si ces effets pouvaient être qualifiés de « naturels » reste matière à débat. Cependant, il est clair que les perturbations provoquées par les pratiques culturales des colons européens à partir du début du XIX e siècle et l'avènement, observé au cours des 50 dernières années, d'une économie fondée sur l'exploitation des ressources, ont eu des conséquences écologiques catastrophiques. Les prairies sont aujourd'hui presque entièrement cultivées, et les portions qui subsistent ont été perturbées par le pâturage ou gravement fragmentées par les routes, les corridors énergétiques ou l'urbanisation. Le présent chapitre traite principalement des changements anthropiques survenus dans les prairies depuis l'arrivée et l'installation des Européens.
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Spiders are the seventh most diverse order of arthropods globally and are prominent predators in all prairie habitats. In this chapter, a checklist for the spiders of the Prairie Provinces (767 recorded species and 44 possible species) is presented along with an overview of all 26 families that occur in the region. Eighteen of the species from the region are adventive. Linyphiidae is by far the dominant family, representing 39% of all species in the three provinces. Gnaphosidae and Lycosidae each represent 8% and three other families (Salticidae, Dictynidae, and Theridiidae) each account for 7%. A summary of biodiversity studies conducted in the Prairies Ecozone and from transition ecoregions is also provided. The Mixed Grassland Ecoregion has the most distinctive assemblage; Schizocosa mccooki and Zelotes lasalanus are common only in this ecoregion. Other ecoregions appear to harbour less distinctive assemblages, but most have been poorly studied. Lack of professional opportunities for spider systematists in Canada remains a major barrier to the advancement of the taxonomy and ecology of spiders.
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Bees (Hymenoptera: Apoidea, Apiformes) are taxonomically and ecologically diverse, with a wide range of social complexity, nesting preferences, floral associations, and biogeographic restrictions. A Canadian bee checklist, greatly assisted by the gene-assisted approach of DNA barcoding, is nearing completion. Previous evaluation of bee diversity in Canada, assisted by DNA barcoding, was restricted to Nova Scotia, which contains about 25% of the bee species in the country. Here, we summarise efforts to date to build a comprehensive DNA barcode library supporting bee taxonomic studies in Canada, consisting of more than 12 500 barcode-compliant sequences yielding 811 distinct barcode index numbers (BINs). This appears to represent ~ 95%of the 856 bee species presently recorded from Canada, but comparison with known morphological species in each genus shows that some genera are still under-sampled or may contain cryptic taxa, with much taxonomic work still to be done on bees in Canada. This is particularly true within the taxonomically difficult genera Andrena Fabricius (Andrenidae), Hylaeus Fabricius (Colletidae), Melissodes Latreille (Apidae), Nomada Scopoli (Apidae), Osmia Panzer (Megachilidae), and Sphecodes Latreille (Halictidae). DNA analysis will likely be a key asset in resolving bee taxonomic issues in Canada in the future, and to date has even assisted studies of well-known bee taxa. Here we present summaries of our results, and discuss the use of DNA barcoding to assist future taxonomic work, faunal lists, and ecological studies.
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For 40 years, the Biological Survey of Canada (BSC) has encouraged and organised studies of the arthropod fauna of Canada, through the wide involvement of the scientific community and the leadership of an expert steering committee. The benefits of the BSC to science include the completion of major cooperative projects to acquire and synthesise knowledge (documenting faunas in the Yukon, Canadian grasslands, and other significant regions and habitats), the assembly and organisation of information and specimens, and improved communication among entomologists. Its efforts have led to valuable monographs, scientific briefs, newsletters, and other products summarised here, including documents that are also useful to those outside entomology. Key operating principles of the BSC are identified. In particular, decisions come from broadly based scientific considerations, an approach to understanding the fauna that guarantees the scientific relevance of the work and is not offset by political or other influences. Core work is planned over the long term to ensure collaboration, focus, efficiency, integrity, quality, productivity, and delivery. The achievements of the BSC over many years confirm the effectiveness of this model for scientific cooperation.
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Four hundred and twelve species of Canadian and Alaskan Collembola arranged in 16 families and 83 genera are listed with all known provincial and state records. Species of questionable status or those identified only to genus were omitted. -from Author
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The authorization of veterinary medicinal products (VMP) requires that they be assessed for non-target effects in the environment. Numerous field studies have assessed these effects on dung organisms. However, few studies have examined effects on soil-dwelling organisms, which might be exposed to VMP residues released during dung degradation. We compared the abundance of earthworms and springtails in soil beneath dung from untreated cattle and from cattle treated 0, 3, 7, 14, and 28 d previously with ivermectin. Study sites were located in different ecoregions in Switzerland (Continental), The Netherlands (Atlantic), France (Mediterranean), and Canada (Northern Mixed Grassland). Samples were collected using standard methods from one to twelve months after pat deposition. Ivermectin concentrations in soil beneath dung pats ranged from 0.02 (3 months) to typically less than 0.006 (5-7 months) mg/kg dry weight. Earthworms were abundant and species-rich at the Swiss and Dutch sites, less common with fewer species at the French site, and essentially absent at the Canadian site. Diverse but highly variable communities of springtails were present at all sites. Overall results showed little effect of residues on either earthworms or springtails. We recommend that inclusion of soil organisms in field studies to assess the non-target effects of VMPs be required only if earthworms or springtails exhibit sensitivity to the product in laboratory tests. This article is protected by copyright. All rights reserved.
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Mean monthly maximum, minimum and mean surface temperatures are analysed for 131 locations in Canada for the period 1895 to 1989. These data were obtained from the Historical Canadian Climate Database (HCCD). There has been a statistically significant rise in mean annual national temperatures over the past century of about l.l0c. Annual mean maximum and minimum national temperature trends since 1895 show a significant increase in mostly-daytime maximum temperatures of about 0.7°C and a highly significant increase in mostly-nighttime minimum temperatures of about 1.5° C. Mean maximum and minimum temperature trends since 1895 are also examined seasonally and regionally and indicate significant increases in minimum temperatures mainly during the spring and summer seasons in the western, northwestern and eastern continental regions of the country. Few significant regional increases are evident in maximum temperatures during any season for this period. Significant decreases in mean temperature range, an important measure of climate variability, occur in most regions during all seasons. Mean maximum and minimum national temperature trends for the past 40 years, since 1950, are also examined. They indicate no significant increases in either minimum or maximum temperatures annually or seasonally. Mean maximum and minimum regional temperature trends since 1950 indicate significant increases in both minimum and maximum temperatures mostly during the spring season in the western and northwestern regions of the country. RESUME Les moyennes mensuelles des temperatures de surface maximales, minimales et moyennes sont analysees pour 131 stations du Canada pour la periode allant de 1895 a 1989. Ces donnees proviennent de la Base de donnees climatiques canadiennes historiques (BDCCH). Ce dernier siecle, il y a eu une hausse statistiquement importante des temperatures nationales annuelles moyennes, hausse d'environ 1,1 DC. Depuis 1895, les tendances de la moyenne annuelle des temperatures nationales maximales et minimales indiquent une nette augmentation, d'environ 0,7 DC, dans les temperatures maximales 63 enregistrees surtout pendant Ie jour et une hausse tres signilicative, d'environ 1,5 °C, des temperatures minimales enregistrees surtout pendant la nuit. Depuis 1895, les tendances des temperatures maximales et minimales moyennes sont aussi examinees par saison et region et revelent d'importantes hausses de la temperature minimale survenant surtout pendant les saisons du printemps et de l'ete dans les regions interieures ouest, nord-ouest et est de la partie continentale du pays. Pendant cette periode, il n'apparmt guere de hausses regionales importantes dans les temperatures maximales. Les baisses signilicatives de la gamme de temperature moyenne, importante mesure de la variabilite climatique, se presentent dans la plupart des regions et pendant toutes les saisons. En outre, on examine les tendances de la moyenne des temperatures nationales maximales et minimales des 40 dernieres annees, depuis 1950. Elles ne revelent aucune hausse importante, annuelle ou saisonniere, des temperatures minimales ou maximales. Les ten dances de la moyenne des temperatures regionales maximales et minimales, depuis 1950, indiquent d'importantes hausses dans les temperatures tant minimales que maximales, surtout pendant la saison du printemps dans I'ouest et Ie nord-ouest du pays.
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This chapter describes the Elateridae of Alberta (144 species), Saskatchewan (108 species), and Manitoba (109 species). It provides current names for species, as well as synonymized names that persist in the literature. Also discussed are the species that have been left out during recent changes to elaterid renaming and classification, although no new name combinations are given. The chapter outlines species distributions, biogeography where known, and the life histories of five common species: Aeolus mellillus (Say), Agriotes mancus (Say), Hypnoidus bicolor (Eschscholtz), Limonius californicus (Mannerheim), and Selatosomus aeripennis destructor (Brown). An examination of the seasonal movements and activity of larvae in response to soil temperature and moisture and moulting cycles is followed by an overview of past research on Prairie Province species. The chapter concludes with a discussion of current research needs and management issues.
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This checklist records the occurrence of 1413 species of spiders (Araneae) in 43 families in Canada and Alaska. Distributions of species are given by state, territory and province. Each species name is presented in its original combination, followed by primary synonyms, if any. The list is dominated by members of the family Linyphiidae (39.5% of total species). Highest numbers of species are recorded for Ontario (746), British Columbia (700) and Québec (677). We record 69 species that are thought to be introduced from elsewhere and 321 that are known in the Palaearctic.
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This chapter lists 81 species of biting flies from the families Culicidae, Ceratopogonidae (genus Culicoides), and Tabanidae for the Canadian Prairies. Twenty-five 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. Identification of the Culicidae and Tabanidae is facilitated by the availability of excellent identification resources. Identification of the genus Culicoides is hampered by the lack of a unified key for western Canada. Despite this, there are many opportunities for investigators to increase knowledge of these groups in Canadian grasslands.