Myriapoda of Canada.

The currently documented fauna of described species of myriapods in Canada includes 54 Chilopoda, 66 Diplopoda, 23 Pauropoda, and two Symphyla, representing increases of 24, 23, 23, and one species, respectively, since 1979. Of the 145 myriapod species currently documented, 40 species are not native to Canada. The myriapods have not been well documented with DNA barcodes and no barcodes are available for Pauropoda. It is conservatively estimated that at least 93 additional myriapods species will be discovered in Canada: Chilopoda (40), Diplopoda (29), Pauropoda (17), and Symphyla (seven). In general, there is a serious dearth of knowledge about myriapods in Canada, and systematics research and surveys continue to be needed to help document the diversity and distribution of these groups in the country.

Introduction

The subphylum contains four extant, monophyletic classes, all of which have representatives in Canada and on all continents except Antarctica: (millipedes), (centipedes), (pauropods), and (garden PageBreakcentipedes or pseudocentipedes). Phylogenetic relationships among myriapod classes have been largely unsettled in recent years; however, the most recent phylogenomic analyses based on morphological and molecular data show strong support for and as sister groups (=Dignatha), with most closely related to Dignatha, and most basal (Fernández et al. 2018).

The earliest records of myriapods from Canada are two species of millipedes described by Newport (1844) based on material in the British Museum: (now ) and (now ). Wood (1862) published the first record of a centipede from Canada, describing based on material from Fort Simpson, Northwest Territories. This material was collected by the explorer and naturalist Robert Kennicott between 1859 and 1862 during his expedition to the Canadian north. No additional myriapod species had been recorded from Canada by 1865 as Wood (1865) listed only the three aforementioned species in his treatise on the of North America. Brodie and White (1883) provided the first checklist of myriapods of Canada and listed five centipede and five millipede species from the country. Three species of and nine of were collected by Geological Survey of Canada personnel (mainly by JB Tyrrell) in 1882–1883 (Chamberlin 1920). Only two of these species were included in the list of Brodie and White (1883). These collections were from British Columbia, Alberta, Ontario, and Quebec and included three millipede species new to science with two type localities in Alberta (Bow River, Waterton Lake) and one in British Columbia (Columbia Valley). Other early country records were reported by Bollman (1887) who described one species of millipede and one centipede from Glacier, British Columbia, although the dates of collection were not indicated.

In Canada, all four classes of myriapods are relatively poorly studied as there has been relatively little sampling of the fauna in the country and there hasn’t been anyone in Canada who has focused on the systematics of these groups. is the best known of the four classes. There are numerous and samples from Canada awaiting identification in Canadian collections. In contrast, and , which are small in size and live in cryptic habitats, are very poorly represented in Canadian collections, so knowledge of the fauna and its distribution and ecology is fragmentary. All four classes of myriapods were briefly summarized in Canada and its insect fauna (Danks 1979), with 47 reported species of (Hoffman 1979), 29–31 of (Kevan 1979), one of (Scheller 1979b), and none of (Scheller 1979a). The number of documented species in Canada has increased since 1979 for all groups. Kevan and Scudder (1989) provided illustrated keys to families of Canadian myriapods, which are still useful despite the more recent addition of several newly recorded families and a modified family structure for some and (Tables 1, 2).

Table 1.

Census of in Canada.

Taxon1	No. species reported in Kevan (1979)2	No. species currently known from Canada3	No. BINs4 available for Canadian species	Est. no. undescribed or unrecorded species in Canada	General distribution by ecozone5	Information sources6
Order Geophilomorpha
Geophilidae 7	10	16 (6)	13	10	most ecozones	Carl and Guiguet 1956; CNCI
Himantariidae	1	1 (1)	0	1	Boreal Shield
Mecistocephalidae	0	0	0	1
Schendylidae	1	2 (1)	5	2	Boreal Shield, Mixedwood Plain, Taiga Cordillera, Boreal Cordillera	Pereira and Hoffman 1993; CNCI
Order Lithobiomorpha
Henicopidae	2	2 (1)	4	3	Pacific Maritime, Prairies, Taiga Plains, Montane Cordillera
Lithobiidae	12	27 (3)	37	20	most ecozones	CNCI
Order Scolopendromorpha
Cryptopidae	2	3 (3)	0	2	Pacific Maritime, Boreal Shield, Mixedwood Plains	Shelley 2002a
Scolopocryptopidae	1	2 (1)	0	1	Pacific Maritime, Mixedwood Plains	Shelley 2002a
Order Scutigeromorpha
Scutigeridae	1	1 (1)	1	0	domiciliary in several ecozones
Total	30	54 (17)	60	40

Classification follows that indicated in Chilobase 2.0 (Bonato et al. 2016). This does not include species listed by Kevan (1979) as “probable”. The numbers in parentheses represents the number of non-native species included in the total. Barcode Index Number, as defined in Ratnasingham and Hebert (2013). BIN data were extracted from BOLD on August 20, 2018. 5See figure 1 in Langor (2019) for a map of ecozones. Literature published before 1979 is usually not included, with one exception, as it was considered by Kevan (1979, 1983a). Kevan (1983a), Kevan and Scudder (1989), Behan-Pelletier (1993) and Mercurio (2010) are applicable to most families but are not listed in the table due to space considerations. CNCI refers to specimens present in the Canadian National Collection of Insects, Arachnids and Nematodes, Ottawa, Ontario. Includes , and .

Table 2.

Census of in Canada.

Taxon1	No. species reported in Hoffman (1979)2	No. species currently known from Canada3	No. BINs4 available for Canadian species	Est. no. undescribed or unrecorded species in Canada	General distribution by ecozone5	Information sources6
Order Polyxenida
Polyxenidae	1	2 (1)	2	0	Atlantic Maritime, Mixedwood Plains, Pacific Maritime
Order Glomeridesmida
Glomeridesmidae	0	0	0	1	Pacific Maritime	Shelley et al. 2007a
Order Polyzoniida
Hirudisomatidae	?	1	2	0	Pacific Maritime	Shelley 1995, 1996
Polyzoniidae	?	2	1	0	Boreal Shield, Mixedwood Plains
Sub-total Polyzoniida	2	3	3	0
Order Julida
Superfamily Blaniuloidea
Blaniulidae	?	5 (5)	2	0	widespread south of taiga ecozones	Shelley and Smith 2011
Okeanobatidae	?	1	0	0	Boreal shield, Mixedwood Plains
Superfamily Juloidea
Julidae	?	8 (8)	26	1	widespread south of taiga ecozones	Shelley and Whitney 1994, Shelley and Smith 2011
Superfamily Nemasomatoidea
Nemasomatidae	?	1	3	1	Montane Cordillera, Pacific Maritime	Enghoff 1985
Superfamily Paeromopodoidea
Paeromopodidae	0	0	0	2	Montane Cordillera, Pacific Maritime
Superfamily Parajuloidea
Parajulidae	?	12	1	4	widespread south of taiga ecozones	Carl and Guiguet 1956, Shelley and Smith 2016
Total Julida	20	27 (13)	32	8
Order Spirobolida
Spirobolidae	1	1	1	0	Boreal Shield, Mixedwood Plains	Shelley et al. 2006
Order Spirostreptida
Cambalidae	0	0	0	2	Pacific Maritime
Order Callipodida
Abacionidae	0	0	0	2	Mixedwood Plains
Order Chordeumatida
Suborder Craspedosomatidea
Superfamily Anthroleucosomatoidea
Anthroleucosomatidae	0	0	0	1	Pacific Maritime
Superfamily Brannerioidea
Branneriidae	0	0	0	1	Mixedwood Plains
Microlympiidae	0	0	0	1	Pacific Maritime
Tingupidae	0	0	0	1	Pacific Maritime	Shear and Shelley 2007, Shelley et al. 2009b
Superfamily Cleidogonoidea
Cleidogonidae	0	0	4	2	Mixedwood Plains
Trichopetalidae	?	1	0	0	Atlantic Maritime, Mixedwood Plains, Newfoundland Boreal	Shear 2010
Superfamily Craspedosomatoidea
Craspedosomatidae	?	1 (1)	2	0	Mixedwood Plains	Shelley 1990b, Hoffman 1999
Suborder Heterochordeumatidea
Superfamily Heterochordeumatidea
Conotylidae	?	6	0	3	widespread south of taiga ecozones	Shelley and LeSage 1996, Shear 2004, Shelley et al. 2009a
Suborder Striadiidea
Superfamily Caseyoidea
Caseyidae	?	4	0	0	widespread south of taiga ecozones	Shelley 1993, Shelley et al. 2007b, 2009
Urochordeumatidae	0	0	0	1	Pacific Maritime	CNCI
Superfamily Stiarioidea
Rhiscosomididae	?	1	0	0	Pacific Maritime	Shelley 1990a, Shelley et al. 2009a
Striariidae	0	0	0	1	Pacific Maritime
unplaced Chordeumatida			7
Total Chordeumatida	6	17 (1)	13	6		BOLD7
Order Polydesmida
Suborder Leptodesmidea
Superfamily Xystodesmoidea
Xystodesmidae	?	6	6	3	Mixedwood Plains, Montane Cordillera, Pacific Maritime,	Shelley 1990a, Shelley et al. 2009a, Marek et al. 2014, Shelley and Smith 2018
Suborder Polydesmidea
Infraorder Polydesmoides
Superfamily Polydesmoidea
Macrosternodesmidae	0	3 (1)	2	0	Pacific Maritime, Montane Cordillera, Newfoundland Boreal	Carl and Guiguet 1956, Whitney and Shelley 1995, Shelley 1994
Polydesmidae	?	10 (4)	4	2	widespread south of taiga ecozones	Judd 1967, Shelley 1996, 2007, Shelley and Smith 2011, Shelley and Snyder 2012
Suborder Strongylosomatidea
Paradoxosomatidae	0	1 (1)	2	0	Atlantic Maritime, Mixedwood Plains, Newfoundland Boreal, Pacific Maritime	Judd 1967, Shelley 1990a
Total Polydesmida	17	20 (6)	14	5
Total	47	66 (21)	65	29

Classification follows that indicated in Millibase (www.millibase.org/index.php) with the exception that is included as a subfamily of which is placed in as suggested by Shear and Reddell (2017). Hoffman (1979) provided species tallies only by order. Thus, many family level tallies are not available. The numbers in parentheses represents the number of non-native species included in the total. Barcode Index Number, as defined in Ratnasingham and Hebert (2013). BIN data were extracted from BOLD on August 20, 2018. See figure 1 in Langor (2019) for a map of ecozones. Literature published before 1979 is usually not included, with one exception, as it was considered by Hoffman (1979) and Kevan (1983b). Kevan (1983b), Kevan and Scudder (1989), Behan-Pelletier (1993), Hoffman (1999), and Shelley (1988, 2002b) are applicable to most families but are not listed in the table due to space considerations. CNCI refers to specimens present in the Canadian National Collection of Insects, Arachnids and Nematodes, Ottawa, Ontario. BOLD: Barcode of Life Data Systems (http://www.boldsystems.org/).

All four myriapod classes are associated with soils and epigaeic habitats, and at least some and are associated with rotting wood. Centipedes are largely predaceous and are venomous (Undheim et al. 2015). The other three classes are largely detritivores, although a few millipedes are known to consume living or dead animal tissue (Hoffman and Payne 1969). Some symphylans feed on roots (fine roots and root hairs) and can damage plants, including crops (Beirne 1972).

The current synopsis is based on literature records, examination of authoritatively identified material in a few Canadian collections, and DNA barcode data in the Barcode of Life Data System (BOLD) database (Ratnasingham and Hebert 2007; http://www.boldsystems.org/). Species lists have not been included in this work but are available from the corresponding author upon request.

The statement, “The centipedes are among the least studied of the larger Canadian arthropods…” is lamentably just as true now as it was 38 years ago when Kevan (1979) wrote it to introduce his treatment of the of Canada. While the Canadian fauna is somewhat better known today, it is estimated that only a little more than half of the Canadian fauna is documented (Table 1). This relatively poor state of knowledge is attributed to the weak taxonomic foundation for in North America in general, and the paucity of effort focused on surveying and documenting the Canadian centipede fauna. These two causes are undoubtedly interlinked as the lack of a solid taxonomic foundation and identification tools for most groups of North American centipedes likely does not engender interest in the group by professional and amateur taxonomists.

A few chilopodologists made enormous strides in the 20th century to describe North American species. For example, of the 556 native species of centipedes reported from North America by Mercurio (2010), 405 were described by Ralph Chamberlin and 21 by Ralph Crabill. Unfortunately, however, there is a distinct shortage of modern taxonomic revisions, and many genera and some families remain inadequately circumscribed. One notable exception is the relatively small order which, thanks largely to the efforts of Rowland Shelley, is relatively well studied in North America, and modern illustrated keys to species are available (e.g., Shelley 2002a). An annotated catalog of the centipedes of North America (Mercurio 2010) is of enormous help to those interested in working on this group. Furthermore, the well-illustrated key to myriapod orders and families in Canada (Kevan and Scudder 1989) is a useful resource to help those interested in chilopod identification. The on-line database, Chilobase 2.0 (Bonato et al. 2016; http://chilobase.biologia.unipd.it/) contains much current information about the classification and nomenclature of , but it is incomplete with respect to the distribution of the North American fauna. Thus, those interested in the general distribution of North American centipedes should consult Mercurio (2010). For the , Bonato and Minelli (2014) provide an overview of the order in Europe, which is the most current source of information about non-native species of this order in North America. Bonato et al. (2012) provide an overview of the relatively large genus , which has representation in Canada, and resolves a number of taxonomic and nomenclature problems within this genus and related genera. The illustrated synopsis of anatomical terminology for centipedes is useful for those working on taxonomy and identification (Bonato et al. 2010).

In Canada, centipedes have received very little attention taxonomically or ecologically. From the publication of the first checklist of Canadian species (Brodie and White 1883)PageBreakPageBreak, it was almost a century before the next synopsis of the Canadian fauna (Kevan 1979), although there was an earlier review of the fauna of Newfoundland (Palmén 1954), the only Canadian jurisdiction to receive such an inventory of its centipede fauna. Kevan (1983a) produced a more complete list of species known from Canada and Alaska, and this was updated by Behan-Pelletier (1993). Snyder (2014) provided a synopsis of species known and expected to be present in Canadian grasslands.

Currently, there are 54 species known to be established in Canada, including (Linnaeus) which is limited to human domiciles (Table 1). In comparison, there are 633 species (including non-native species) known from North America (Mercurio 2010) and 3110 species globally (Minelli 2011). The represents the largest proportion of the Canadian fauna (53.7%), followed by (35.2%), (9.3%) and (1.8%), and this proportional representation is very similar to that for the North American fauna as a whole (Mercurio 2010). About 31% of the documented Canadian fauna is not native compared to 12% for the North American fauna (Mercurio 2010). Undoubtedly other non-native species are established in Canada but are yet undocumented.

Compared to the 1979 assessment, the number of species documented in Canada has increased by 24 (80%), with the greatest increases within the families and . Most of the changes to the fauna since 1979 were reported by Kevan (1983a) and Behan-Pelletier (1993), and mainly represent Canadian species occurrences already reported in earlier literature that were missed by Kevan (1979). All of these authors, however, overlooked the records of two , Chamberlin and (Chamberlin), recorded from Bunsby Islands, British Columbia by Carl and Guiguet (1956), the specimens of which were identified by Chamberlin. With the exception of the , our collective knowledge of the diversity and distribution of Canadian centipedes has not increased much over the last 25 years. While most major terrestrial arthropod collections in Canada contain small-to-moderate numbers of centipede samples, the majority of those are not authoritatively identified. Most Canadian records come from southern Quebec, Ontario, British Columbia, and the island of Newfoundland, the latter thanks to the Fennoscandinavian expeditions of 1949 and 1951 as reported by Palmén (1954). All ecozones of Canada are poorly known in terms of their centipede faunas.

The number of additional species expected to be in Canada but yet undocumented (either undiscovered or undescribed) was estimated by examination of the distribution of species reported in Mercurio (2010) and references contained therein. Some species collected in the USA within 100 km of the Canadian border, and which have broad distributions in the USA (i.e., not likely to be local endemics), were deemed to be likely present in Canada and this forms the basis of the conservative estimate of undocumented species for Canada (Table 1). Thus, it is estimated that 43% of the Canadian fauna (40 species) is yet undocumented, mostly members of the families and (Table 1).

The generation of DNA barcodes for Canadian centipedes is still in the early stages as material has been provided from only a small number of specimens and localities. PageBreakNonetheless, 60 Barcode Index Numbers (BINs; see Ratnasingham and Hebert 2013) are represented based on Canadian specimens (Table 1). In the , , and there are more BINs than documented species, which may be indicative of undocumented species diversity. Clearly much work remains to fully document the Canadian fauna of centipedes.

The taxonomic foundation for reliably identifying found in Canada is in much better shape than for . Fortunately, there has been considerable taxonomic research in the USA, especially by Ralph Chamberlin, Nell Causey, Richard Hoffman, Petra Sierwald, William Shear, and Rowland Shelley, that has greatly aided knowledge of the Canadian fauna. Nonetheless, many families can benefit from modern taxonomic revisions that consider molecular and morphological characters. A catalogue of North and Middle American is available (Hoffman 1999) and, although now almost 20 years old and a bit dated, is still an enormously helpful resource. The on-line database Millibase (www.millibase.org/), which covers the global fauna, is also a helpful resource but is incomplete with respect to capturing published knowledge about the Canadian fauna.

As with , there has been a dearth of targeted survey work on millipedes in most of Canada so the fauna of all ecozones is incompletely known. The only Canadian jurisdiction that experienced a faunal inventory is the island of Newfoundland, which was extensively surveyed during the Fennoscandinavian expeditions of 1949 and 1951 (Palmén 1952). Beyond that, most current Canadian records are from southwestern British Columbia and southern Ontario and Quebec. The Canadian fauna was summarized by Hoffman (1979) who reported 47 species in 15 families and six orders; however, the species numbers were reported only at the order level and no species list was included. Furthermore, he predicted that another 22–23 species likely occurred in Canada for a total fauna of 69–70 species. Shortly thereafter, and based on literature records and authoritative examination of holdings of some Canadian collections, Kevan (1983b) published a list of 65 species known from Canada, several of which were subsequently synonymized and others identified only to genus. Shelley (1988) published a species list for eastern Canada (Ontario and eastward), including 38 species. Shelley (1990a) gave distributions for species in British Columbia. Kevan and Scudder (1989) published some faunal updates and Behan-Pelletier (1993) provided a revised list of species in Canada and their known provincial and territorial distributions. The most recent treatment of the Canadian fauna was by Shelley (2002b) who reviewed the central Canadian fauna (Alberta, Saskatchewan and Manitoba) in detail and also provided a list of the known and expected species for the entire country that included 62 recorded species and another 11 species that were considered likely in Canada based on distributions in the USA.

Currently, there are 66 described species in 18 families and six orders known in Canada (Table 2), in comparison to ~1500 species known from North America (an PageBreakPageBreakPageBreakPageBreakestimate based mainly on information in Hoffman (1999)) and 15,982 species known globally (Sierwald and Spelda 2018). The represents about 18.2% of the described Canadian fauna, followed by (15.2%) and (12.1%). About 32% of the described Canadian fauna is non-native compared to only 2% for the North American fauna (Snyder and Hendrix 2008); however, this high proportion is likely because a large portion of the native Canadian fauna is unknown. The current species total is a 40% increase over that reported by Hoffman (1979), highlighting a substantial increase in knowledge of the fauna over the last ca. 40 years. In addition to described species, material has been collected in Canada representing four additional families (, , , and ; Table 2) but it is not known if this material represents described species. Taking into account this unidentified material, the opinion of Shelley (2002b) concerning species likely to be present in Canada, and supplemented by examination of species distributions documented in subsequent publications about the North American fauna, we conservatively estimate that at least 29 additional species reside in Canada, including seven additional families. This means that Canada should have a millipede fauna of at least 95 species and is thus roughly equivalent to the estimated species richness of the Canadian centipede fauna (94 species; Table 1). However, as there are about three times as many millipedes as centipedes known from North America (Snyder and Hendrix 2008, Mercurio 2010), the Canadian millipede fauna is likely to be much more diverse than estimated herein.

Only 65 BINs representing 14 of the 22 families of millipedes known from Canada are available (Table 2), and only 12 BINs are associated with material identified to species level. Clearly, much work remains to adequately barcode Canadian millipedes. Notably, 26 BINs are associated with , a family not native to Canada, which is much higher than the eight documented species recorded from Canada.

The ecology of millipedes has received little attention in Canada; however, in a study of the influence of Wood on litter decomposition in the coastal forests of British Columbia, Cárcamo et al. (2000) found that this species consumed as much as 36% of the annual litter fall.

Pauropods are soft-bodied, small (0.5–2.0 mm long) detritivores found in soils (Scheller 1979a). Worldwide there are about 835 known species (Scheller 2011a), and about 100 species are known from the USA (Scheller 2011b), however, the fauna is poorly documented at both regional and global scales (Scheller 2011a, b). The Canadian fauna is poorly known in terms of species composition, distribution, and ecology, although some progress has been made since 1979. The earliest record from Canada is from the Yukon where Hilton (1931) described a new species, ; however, as his type material is considered lost and the description is very superficial, this species is considered to be nomen dubium (Scheller 1984). Scheller (1979a) reported no named PageBreakPageBreakspecies from Canada but estimated that around 20 species could be found there. Based on examination of 320 specimens from three Canadian collections in British Columbia, Ontario and Quebec, Scheller (1984) reported 23 species in two families (Table 3) from those three provinces, including six species new to science, and also provided keys to known families and genera in Canada. It is possible that four species are non-native based on known distribution. Six additional species have wide distributions (cosmopolitan in some cases) and some of these may also be non-native in Canada. This material could not be located in Canadian collections so may still be in the private collection of Ulf Scheller in Sweden. No new species have since been reported from the country. Also, no Canadian specimens of have been DNA barcoded.

Table 3.

Census of in Canada.

Taxon1	No. species currently known from Canada2	No. BINs3 available for Canadian species	Est. no. undescribed or unrecorded species in Canada	General distribution by ecozone4	Information sources
Order Tetromerocerata
Brachypauropodidae	1 (0)	0	4	Pacific Maritime	Scheller 1984, 1985, 1986a
Eurypauropodidae	0	0	2		Scheller 1985
Pauropodidae	22 (4)	0	11	Boreal Shield, Mixedwood Plains, Pacific Maritime, Western Interior Basin	Scheller 1984, 1985, 1986a
Total	23 (4)	0	17

Classification that of Scheller (2008). The numbers in parentheses represents the number of non-native species included in the total. Barcode Index Number, as defined in Ratnasingham and Hebert (2013). BIN data were extracted from BOLD on August 20, 2018. See figure 1 in Langor (2019) for a map of ecozones.

Based on a survey of the literature treating in the continental USA (Scheller 1985 and references therein) and Alaska (Scheller 1986a), it is conservatively estimated that at least 17 additional species and one additional family () will be found in Canada (Table 3).

It is clear from a quick inventory of some major Canadian collections that pauropods have been seldom collected and preserved in Canada as there is little material accessioned. Records exist for only British Columbia, Ontario, Quebec and Yukon. In Alberta, the Alberta Biodiversity Monitoring Institute has been conducting a systematic survey of soil fauna across the entire province on a 20 km × 20 km grid since 2007. In support of this provincial-scale survey, taxonomists at the Royal Alberta Museum extract approximately 800 soil samples each year for invertebrates, particularly oribatid mites. A recent census of residual material from 194 of these samples yielded no or (T Cobb pers. comm.), underscoring the difficulty in collecting these organisms using soil cores. By comparison, and were extracted from about 2% of samples.

are also small (1–10 mm long) soil-dwellers and are usually infrequently collected. However, the most wide-spread species in Canada, the non-native and cosmopolitan (Newport), can be abundant in greenhouses and outdoors in more moderate climates and can cause significant damage to roots of many vegetable crops especially in southern British Columbia and Ontario (Beirne 1972).

is the least diverse class of myriapods with about 35 species known from North America (Scheller 1986b) and 195 globally (Szucsich and Scheller 2011). Scheller (1979b) reported one species from Canada, , which is now likely to be distributed across southern Canada from coast to coast (Beirne 1972, Morris and Morry 1983). Subsequently, Kevan (1983a) reported the cosmopolitan and likely introduced (Hansen) based on a specimen in the Lyman Entomological Museum (McGill University) collected from a southern Quebec hardwood forest. Since then, no more species have been recorded from Canada, although undoubtedly additional species occur here. In addition to reporting one species, Scheller (1979b)PageBreakestimated about 10 undocumented species in Canada. Kevan (1983b) mentions seven species and one more family () that are likely in Canada (Table 4) and we adopt his estimate herein. Only four specimens from Canada have been DNA barcoded and each represents a different BIN, three within and one within (Table 4).

Table 4.

Census of in Canada.

Taxon1	No. species reported in Scheller (1979b)	No. species currently known from Canada3	No. BINs2 available for Canadian species	Est. no. undescribed or unrecorded species in Canada	General distribution by ecozone3	Information sources4
Order Cephalostigmata
Geophilellidae	0	0	0	2		Kevan 1983a
Scolopendrellidae	0	1 (1)	3	1	Mixedwood Plains	Kevan 1983a
Scutigerellidae	1	1 (1)	1	4	likely all ecozones south of taiga and Boreal Cordillera	Beirne 1972, Kevan 1983a, Morris and Morry 1983; BOLD
Total	1	2 (2)	4	7

Classification follows that of Millibase (www.millibase.org/index.php). Barcode Index Number, as defined in Ratnasingham and Hebert (2013). BIN data were extracted from BOLD on August 20, 2018. See figure 1 in Langor (2019) for a map of ecozones. BOLD: Barcode of Life Data Systems (http://www.boldsystems.org/).

Gaps and opportunities

Given the paucity of knowledge about the faunal composition, taxonomy, distribution, and ecology of all myriapod classes in Canada, there are plentiful opportunities to add to this body of knowledge by collecting and studying these fascinating creatures. All myriapod classes are poorly sampled over all of Canada, meaning that any specimens encountered are likely to represent useful records. Even the North may have considerable diversity, especially in Beringian areas. Centipedes and millipedes are frequently encountered by turning rocks and logs, picking apart highly rotten logs, sifting dead leaves, and using pitfall traps. and are much less frequently encountered or detected. Sometimes rolling deeply embedded rocks will reveal specimens of these two classes, and sifting of litter is a useful approach. Tullgren and Berlese funnel extractions of organic and mineral soil layers may also yield specimens. We implore those who encounter myriapods to make an effort to preserve specimens in ethanol and accession them into a publically accessible collection. The other challenge with working with myriapods is the poor state of taxonomy and relative paucity of taxonomic resources and local expertise. has a much better taxonomic foundation and better availability of taxonomic resources than the other groups. In North America there are a few people who actively study taxonomy of millipedes. For centipedes there is very little taxonomic work ongoing in North America and for and there is essentially none. We encourage others to seek out, observe, collect and study these fascinating creatures in Canada and more broadly in North America.