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ZooKeys 186: 293–348, doi: 10.3897/zookeys.186.2469
New Staphylinidae (Coleoptera) records with new collection data from New Brunswick and an addition to the fauna of Quebec: Staphylininae
Reginald P. Webster 1, Aleš Smetana 2, Jon D. Sweeney 1, Ian DeMerchant 1
1 Natural Resources Canada, Canadian Forest Service - Atlantic Forestry Centre, 1350 Regent St., P.O. Box 4000, Fredericton, NB, Canada E3B 5P7
2 Agriculture and Agri-Food Canada, Biodiversity, Central Experimental Farm, K. W. Neatby Bldg., Ottawa, ON K1A 0C6

Corresponding author: Reginald P. Webster (reginaldwebster@rogers.com)

Academic editor: J. Klimaszewski

received 30 October 2011 | accepted 20 January 2012 | Published 26 April 2012


(C) 2012 Reginald P. Webster. This is an open access article distributed under the terms of the Creative Commons Attribution License 3.0 (CC-BY), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.


For reference, use of the paginated PDF or printed version of this article is recommended.

Abstract

Forty-four species of Staphylininae are newly reported from New Brunswick, bringing the total number of species known from the province to 126. Quedius criddlei (Casey) is reported for the first time from Quebec. Bisnius cephalotes (Gravenhorst) is removed from the faunal list of New Brunswick due to a lack of supporting voucher specimens. Additional locality data are presented for seven species either recently recorded from the province or with few previous records and little habitat data. We provide the first documented records of Atrecus americanus (Casey), Quedius erythrogaster Mannerheim, Quedius labradorensis labradorensis Smetana, Quedius plagiatus (Mannerheim), and Neobisnius terminalis (LeConte) from New Brunswick. Collection and habitat data are presented and discussed for all species.

Keywords

Staphylinidae, Staphylininae, new records, Canada, New Brunswick, United States, Maine

Introduction

Intensive collecting of rove beetles (family Staphylinidae) in New Brunswick by the first author since 2003 has yielded many new provincial and national records. Additional records were obtained from by-catch samples during a study to develop a general attractant for detecting invasive species of Cerambycidae. These records are being published in a series of papers, each focusing on one or more subfamilies of Staphylinidae and other families of Coleoptera. This paper covers the subfamily Staphylininae.

This subfamily is fairly well known taxonomically in Canada and North America, thanks to various revisions. The genera Erichsonius and Neobisnius were revised by Frank (1975, 1981), respectively. The Xantholinini were revised by Smetana (1982, 1988), the Quediina by Smetana (1965, 1971a, 1971b, 1973, 1976, 1978, 1981, 1990), the Philonthina by Smetana (1995), and the Staphylinina by Brunke et al. (2011). As a result of these revisions, our knowledge of the distribution of these species in Canada was also greatly increased.

Adults of Staphylininae live in a wide variety of habitats. Many species live in and near wetlands, including river and brook margins, lakeshores, vernal pool and pond margins, bogs, marshes, sea beaches, and various synanthropic situations (Smetana 1971a, 1982, 1995). Depending on species, adults usually occur in leaf litter, sphagnum moss, and other kinds of debris in these wetland habitats, but some species are highly hygrophilic and occur in floating mats of moss or vegetation (Smetana 1971a, 1982, 1995). Other species are associated with decaying organic materials, including compost, decaying mushrooms, animal droppings, and carcasses. Some species are regular inhabitants of bird and mammal nests. Philonthus janus Smetana, Philonthus couleensis Hatch, and Quedius campbelli Smetana are commonly found in North American beaver (Castor canadensis Kuhl) lodges and muskrat (Ondatra zibethicus (L.)) nests, but these associations are not strict, and these species can also be found in adjacent wetland habitats (Smetana 1995). However, a few species such as Heterothops marmotae Smetana and Bisnius lautus (Casey) have much stronger associations (Smetana 1971b, 1995). These species live in underground burrows of rodents and are rarely found in other habitats. Most species are probably general predators (Smetana 1995), although additional research is required to elucidate the biology of most members of this subfamily.

Campbell and Davies (1991) reported 27 species of Staphylininae for New Brunswick. The number of species recorded from the province was increased to 77 species as a result of revisions by Smetana (1995), and new additions to the fauna by Klimaszewski et al. (2005), Majka and Smetana (2007), Majka and Klimaszewski (2008a, b), Majka et al. (2009), Majka and Brown (2010), and Smetana and Webster (2011). Majka et al. (2011) reported Atrecus americanus (Casey), Quedius erythrogaster Mannerheim, Quedius labradorensis labradorensis Smetana, Quedius plagiatus (Mannerheim), and Neobisnius terminalis (LeConte) as occurring in New Brunswick but did not provide any supporting references or data for the records. Here, we report an additional 44 species of Staphylininae for New Brunswick, bringing the total number of species known for the province to 126 (Table 1).

Table 1.

Species of Staphylininae (Staphylinidae) recorded from New Brunswick, Canada.

Subfamily Staphylininae Latreille
Tribe Diochini Casey
Diochus schaumi Kraatz**
Tribe Othiini Thomson
Atrecus americanus (Casey)
Atrecus macrocephalus (Nordmann)
Tribe Xantholinini Erichson
Gyrohypnus angustatus Stephens
Gyrohypnus campbelli Smetana*
Gyrohypnus fracticornis (Müller)
Hypnogyra gularis (LeConte)**
Leptacinus intermedius Donisthorpe
Neohypnus beckeri Smetana**
Neohypnus hamatus (Say)
Neohypnus obscurus (Erichson)
Nudobius cephalus (Say)
Oxybleptes kiteleyi Smetana
Phacophallus parumpunctatus (Gyllenhal)**
Stictolinus flavipes (LeConte)
Xantholinus linearis (Olivier)
Xestolinus abdominalis Casey**
Tribe Staphylinini Latreille
Subtribe Quediina Kraatz
Acylophorus (Amacylophorus) pratensis LeConte**
Acylophorus (Acylophorus) caseyi Leng*
Acylophorus (Acylophorus) pronus Erichson
Anaquedius vernix (LeConte)
Hemiquedius ferox (LeConte)*
Heterothops fusculus LeConte
Heterothops minor Smetana*
Heterothops pusio LeConte**
Quedius (Microsaurus) bicoloris Smetana & Webster
Quedius (Microsaurus) campbelli Smetana**
Quedius (Microsaurus) canadensis (Casey)
Quedius (Microsaurus) criddlei (Casey)**
Quedius (Microsaurus) erythrogaster Mannerheim
Quedius (Microsaurus) mesomelinus (Marsham)
Quedius (Microsaurus) peregrinus (Gravenhorst)
Quedius (Microsaurus) spelaeus Horn
Quedius (Quedius) curtipennis Bernhauer
Quedius (Quedius) labradorensis Smetana
Quedius (Quedionuchus) plagiatus (Mannerheim)
Quedius (Distichalius) capucinus (Gravenhorst)*
Quedius (Distichalius) cinctus (Paykull)
Quedius (Raphirus) frigidus Smetana**
Quedius (Raphirus) fulvicollis (Stephens)**
Quedius (Raphirus) rusticus Smetana
Quedius (Raphirus) simulator Smetana**
Subtribe Staphylinina Latreille
Creophilus maxillosus (Linnaeus)
Dinothenarus badipes LeConte
Dinothenarus capitatus (Bland)
Ontholestes cingulatus (Gravenhorst)
Platydracus cinnamopterus Gravenhorst
Platydracus cupripennis (Melsheimer)
Platydracus fossator (Gravenhorst)
Platydracus viridanus (Horn)
Staphylinus ornaticauda LeConte*
Tasgius ater (Gravenhorst)
Tasgius melanarius (Heer)
Subtribe Xanthopygina Sharp
Tympanophorus puncticollis Erichson
Subtribe Philonthina Kirby
Bisnius blandus (Gravenhorst)
Bisnius cephalicus (Casey)**
Bisnius palmi (Smetana)*
Bisnius quediinus (Horn)**
Bisnius siegwaldii (Mannerhiem)
Bisnius sordidus (Gravenhorst)
Cafius bistriatus Erichson
Erichsonius alumnus Frank**
Erichsonius inutilis (Horn)**
Erichsonius nanus (Horn)
Erichsonius parcus (Horn)**
Erichsonius patella (Horn)*
Erichsonius pusio (Horn)**
Erichsonius rosellus Frank**
Gabrius appendiculatus Sharp
Gabrius astutoides (A. Strand)
Gabrius brevipennis (Horn)
Gabrius fallaciosus (Horn)**
Gabrius microphthalmus (Horn)
Gabrius picipennis (Mäklin)
Gabrius ulpius Smetana*
Hesperus apicialis Say**
Laetulonthus laetulus (Say)**
Neobisnius jucundus (Horn)**
Neobisnius lathrobioides (Baudi)**
Neobisnius sobrinus (Erichson)
Neobisnius terminalis (LeConte)
Neobisnius villosulus (Stephens)
Philonthus aequalis Horn**
Philonthus boreas Smetana**
Philonthus caeruleipennis (Mannerheim)
Philonthus carbonarius (Gravenhorst)
Philonthus cognatus Stephens
Philonthus concinnus (Gravenhorst)
Philonthus couleensis Hatch
Philonthus cruentatus (Gmelini)
Philonthus debilis (Gravenhorst)
Philonthus discoideus (Gravenhorst)
Philonthus flavibasis Casey**
Philonthus flumineus Casey
Philonthus furvus Nordman
Philonthus fusiformis Melsheimer
Philonthus gracilior Casey
Philonthus hepaticus Erichson
Philonthus hudsonicus Horn
Philonthus janus Smetana
Philonthus jurgans Tottenham
Philonthus lindrothi Smetana
Philonthus lomatus Erichson
Philonthus monaeses Smetana
Philonthus neonatus Smetana*
Philonthus opacipennis Notman
Philonthus palliatus (Gravenhorst)
Philonthus politus (Linnaeus)
Philonthus pseudolus Smetana**
Philonthus quadricollis Horn
Philonthus rectangulus Sharp
Philonthus schwarzi Horn
Philonthus sericans (Gravenhorst)
Philonthus sericinus Horn**
Philonthus sessor Smetana
Philonthus sphagnorum Smetana
Philonthus spiniformis Hatch
Philonthus stictus Hausen
Philonthus subvirescens Thomson
Philonthus thoracicus (Gravenhorst)
Philonthus umbratilis (Gravenhorst)
Philonthus umbrinoides Smetana*
Philonthus validus Casey
Philonthus varians (Paykull)
Philonthus varro Smetana
Philonthus vulgatus Casey*

Notes: *New to province; **New to Maritime provinces

Methods and conventions

The following records are based in part on specimens collected as part of a general survey by the first author to document the Coleoptera fauna of New Brunswick. Additional provincial records were obtained from specimens contained in the collection at Natural Resources Canada’s Atlantic Forestry Centre in Fredericton, New Brunswick.

Collection methods

Various collection methods were employed to collect the Staphylininae reported in this study. Details are outlined in Campbell (1973) and Webster et al. (2009, Appendix). Many specimens were also collected as by-catch in Lindgren 12-funnel traps (ConTech Inc., Delta, BC) baited with various attractants as part of a study to develop a general attractant for detecting invasive species of Cerambycidae. These traps mimic tree trunks and are often effective for sampling species of Coleoptera that live in microhabitats associated with standing trees (Lindgren 1983). Traps were suspended from rope tied between two trees separated by at least 2 m, with the collecting cup 30–50 cm above the ground. Collecting cups contained either a 50:50 mixture of propylene glycol and deionized water plus 0.5 ml/L of Kodak Photo-Flo 200 and 12.5 mg/L of Bitrex (in 2008) or a saturated salt solution with 1–2 drops of unscented dish detergent (in 2009 and 2010). Traps were baited with various lures reported as pheromones for longhorn species in the Cerambycinae subfamily (racemic 3-hydroxyhexan-2-one or racemic 3-hydroxyoctan-2-one) (Allison et al. 2004; Hanks et al. 2007) and/or high-release-rate ethanol lures (ConTech, Inc, Delta, BC), or were left unbaited. The effects of lure treatment on attraction (capture in Lindgren traps) of Staphylininae species and other by-catch species will be reported in separate papers. Samples were collected once weekly (2008 and 2009) or once every 2 weeks (2010), and specimens frozen until they were processed. A description of the habitat was recorded for all specimens collected during this survey. Locality and habitat data are presented exactly as on labels for each record. This information, as well as additional collecting notes, is summarized in the collection and habitat data section for each species.

Specimen preparation

Examples of most species of Staphylininae were dissected to confirm their identity. The genital structures were dehydrated in absolute alcohol, mounted in Canada balsam on celluloid microslides, and pinned with the specimens from which they originated.

Distribution

Distribution maps, created using ArcMap and ArcGIS, are presented for each species in New Brunswick. Every species is cited with current distribution in Canada and Alaska, using abbreviations for the state, provinces, and territories. New records for New Brunswick are indicated in bold under Distribution in Canada and Alaska. The following abbreviations are used in the text:

AK Alaska MB Manitoba
YT Yukon Territory ON Ontario
NT Northwest Territories QC Quebec
NU Nunavut NB New Brunswick
BC British Columbia PE Prince Edward Island
AB Alberta NS Nova Scotia
SK Saskatchewan NF & LB Newfoundland and Labrador*
*Newfoundland and Labrador are each treated separately under the current Distribution in Canada and Alaska.

Acronyms of collections referred to in this study are as follows:

AFC Atlantic Forestry Centre, Natural Resources Canada, Canadian Forest Service, Fredericton, New Brunswick, Canada

CNC Canadian National Collection of Insects, Arachnids and Nematodes, Agriculture and Agri-Food Canada, Ottawa, Ontario, Canada

CCC C. Chantal Collection, Varennes, Quebec, Canada

NBM New Brunswick Museum, Saint John, New Brunswick, Canada

RWC Reginald Webster Collection, Charters Settlement, New Brunswick, Canada

Results

Forty-four species of Staphylininae are newly recorded from New Brunswick; Bisnius cephalotes (Gravenhorst) is removed from the faunal list of New Brunswick because of lack of a supporting voucher specimen. We provide the first documented records of Atrecus americanus (Casey), Quedius erythrogaster Mannerheim, Quedius labradorensis labradorensis Smetana, Quedius plagiatus (Mannerheim), and Neobisnius terminalis (LeConte) from New Brunswick. This brings the total number of species known from the province to 126 (Table 1). Thirty-three of these species are newly recorded for the Maritime provinces (New Brunswick, Nova Scotia, Prince Edward Island) of Canada. Additional locality data are presented for seven species either recently recorded from the province or having few previous records and little bionomic data. Quedius criddlei (Casey) is reported for the first time from Quebec.

Species accounts

All records below are species newly recorded for New Brunswick, Canada, unless noted otherwise (additional records). Species followed by ** are newly recorded from the Maritime provinces of Canada.

The classification of the Staphylininae follows Bouchard et al. (2011).

Subfamily Staphylininae, Latreille, 1802 Tribe Diochini Casey, 1906
Diochus schaumi Kraatz, 1860**

http://species-id.net/wiki/Diochus_schaumi

Map 1
Material examined.

New Brunswick, York Co., Upper Brockway, 45.5684°N, 67.0993°W, 23.IV.2006, R. P. Webster, forested black spruce bog, in sphagnum. (1, RWC)

Collection and habitat data.

The single New Brunswick specimen was collected from sphagnum in a forested black spruce (Picea mariana (Mill.) B.S.P.) bog. Elsewhere this species has been reported from forest litter and from wet moss and debris in wet habitats, such as swamps, marshes, bogs, and lake and stream margins (Smetana 1982). The single adult was collected by sifting sphagnum during late April.

Distribution in Canada and Alaska.

ON, QC, NB (Smetana 1982).

Map 1.

Collection localities in New Brunswick, Canada of Diochus schaumi

Tribe Othiini Thomson, 1859
Atrecus americanus (Casey, 1906)

http://species-id.net/wiki/Atrecus_americanus

Map 2
Material examined.

Additional New Brunswick records, Albert Co., Caledonia Gorge P.N.A. (Protected Natural Area), at Turtle Creek, 45.8432°N, 64.8411°W, 5.VII.2011, A. Fairweather, old hardwood forest (sugar maple and beech), in rotten log near creek (1, NBM); Caledonia Gorge P.N.A. at Caledonia Creek, 45.7935°N, 64.7760°W, 1.VII.2011, R. P. Webster, shaded, rocky, cold, clear brook, splashing moss on rocks (1, NBM). Carleton Co., Hovey Hill PNA, (Protected Natural Area), 46.1115°N, 67.7770°W, 19.VIII.2007, R. P. Webster, hardwood forest, under bark. (1, RWC); Jackson Falls, Bell Forest, 46.2208°N, 67.7211°W, 10.VII.2004, Vincent Webster & R. P. Webster, mixed forest, in bracket fungi (1, RWC); same locality and forest type but 46.2200°N, 67.7231°W, 13.VIII.2006, R. P. Webster, in decaying fleshy polypore fungi (1, RWC); same locality and forest type, 8–16.VI.2009, 16–21.VI.2009, 19–31.VII.2009, R. Webster & M.-A. Giguère, Lindgren funnel traps (3, AFC). Queens Co., Cranberry Lake PNA, 46.1125°N, 65.6075°W, 21–27.V.2009, 21–28.VII.2009, 28.VII-6 VIII.2009, R. Webster & M.-A. Giguère, mature red oak forest, Lindgren funnel traps (3, AFC). Restigouche Co., Berry Brook PNA, 47.8140°N, 66.7578°W, 26.V.2007, R .P. Webster, old-growth eastern white cedar swamp, in moss on hummock at base of cedar (2 ♂, RWC); Jacquet River Gorge PNA, 47.7491°N, 66.1114°W, 24.VI.2008, R. P. Webster, hardwood forest, under bark (1, NBM). Sunbury Co., Acadia Research Forest, 45.9799°N, 66.3394°W, 14.V.2007, R. P. Webster, mature red spruce and red maple forest, sifting deep conifer litter at base of large red spruce (1, AFC); Acadia Research Forest, 45.9866°N, 66.3841°W, 2–9.VI.2009, 21–29.VII.2009, 29.VII-4.VIII.2009, R. Webster & M.-A. Giguère, mature (110-year-old) red spruce forest with scattered red maple and balsam fir, Lindgren funnel traps (3, AFC). York Co., Charters Settlement, 45.8300°N, 66.7360°W, 1.V.2004, R. P. Webster, mixed forest, under bark of conifer log (1, RWC); same locality data and collector but 21.VI.2004, mixed forest, under bark (1, RWC); same locality and collector but 45.8286°N, 66.7211°W, 10.VII.2005, mature red spruce and cedar forest, in bracket fungi (1 ♂, RWC); Fredericton, Odell Park, 7.IX.2005, 45.9570°N, 66.6695°W, R. P. Webster, old-growth hemlock forest, on bracket fungi (1, RWC); 15 km W of Tracy off Rt. 645, 45.6848°N, 66.8821°W, 1–8.VI.2009, R. Webster & M.-A. Giguère, old red pine forest, Lindgren funnel trap (1, AFC); 14 km WSW of Tracy, S of Rt. 645, 45.6741°N, 66.8661°W, 10–26.V.2010, R. Webster & C. MacKay, coll., old mixed forest with red and white spruce, red and white pine, balsam fir, eastern white cedar, red maple, and Populus sp., Lindgren funnel trap (1, AFC).

Collection and habitat data.

Smetana (1982) reported this species from under bark of dead trees with one record from Fomitopsis pinicola (Swartz: Fr.) Karst. In New Brunswick, this species was found in various forest types, including hardwood, mixed red spruce (Picea rubens Sarg.) and eastern white cedar (Thuja occidentalis L.), and old-growth hemlock (Tsuga canadensis (L.)). Adults were found under bark of both dead hardwood and conifer trees, in rotten logs, and in various species of polypore fungi (fleshy and bracket fungi). One adult was found in moss on a rock along a shaded brook. Adults were collected during May, June, July, August, and September.

Distribution in Canada and Alaska.

ON, QC, NB, NS (Smetana 1982). Atrecus americanus was listed as occurring in New Brunswick by Majka et al. (2011) without any supporting references or data. Here, we provide the first documented records from New Brunswick.

Map 2.

Collection localities in New Brunswick, Canada of Atrecus americanus.

Tribe Xantholinini Erichson, 1839
Gyrohypnus campbelli Smetana, 1982

http://species-id.net/wiki/Gyrohypnus_campbelli

Map 3
Material examined.

New Brunswick, Restigouche Co., Jacquet River Gorge P.N.A, 47.7146°N, 66.1644°W, 24.VI.2008, R. P. Webster, alder swamp adjacent to slow flowing brook, in leaves on muddy soil (1 ♂, NBM). York Co., Charters Settlement, 45.8428°N, 66.7279°W, 19.IV.2005, 28.IV.2004, R. P. Webster, mixed forest, in litter near small sedge marsh (2, RWC); same locality but 45.8395°N, 66.7391°W, 23.IV.2004, 29.IV.2004, 9.V.2005, R. P. Webster, mixed forest near small shaded brook, in forest litter (2 ♂, 3 sex undetermined, NBM, RWC); same locality but 45.8341°N, 66.7445°W, 22.IV.2005, R. P. Webster, mature red spruce and eastern white cedar forest, margin vernal pond in leaf litter (2, RWC); New Maryland, off Hwy 2, E of Baker Brook, 45.8760°N, 66.6252°W, 6.IV.2005, R. P. Webster, old growth eastern cedar swamp in moss and litter on hummock (1, RWC); Rt. 645 at Beaver Brook, 45.6860°N, 66.8668°W, R. P. Webster, Carex marsh, in litter at base of dead red maple (1 ♂, RWC); near Mazerolle Settlement, NE of exit 271, off Hwy 2, 45.8776°N, 66.8254°W, 8.VI.2008, R. P. Webster, alder swamp with poplar, in leaf litter and moss near vernal pool (1, NBM).

Collection and habitat data.

In New Brunswick, adults were usually found in moss, leaf, and grass litter near various kinds of wet habitats. These included Carex marshes, shaded brook margins, a vernal pond in a mature red spruce and eastern white cedar forest, and on hummocks in an old-growth eastern white cedar swamp. Elsewhere, this species has been found in similar habitats, including a series collected from a beaver lodge (Smetana 1982). Adults were collected during April, May, and June.

Distribution in Canada and Alaska.

MB, ON, QC, NB, NS (Smetana 1982; Bishop et al. 2009).

Map 3.

Collection localities in New Brunswick, Canada of Gyrohypnus campbelli.

Hypnogyra gularis (LeConte, 1880)**

http://species-id.net/wiki/Hypnogyra_gularis

Map 4
Material examined.

New Brunswick, Carleton Co., Jackson Falls, Bell Forest, 46.2200°N, 67.7231°W, 18.IX.2006, R. P. Webster, mature hardwood forest, under bark of large dead basswood covered with polypore fungi (1, RWC); same locality and habitat, 20–26.V.2009, R. Webster & M.-A. Giguère, Lindgren funnel trap (1, RWC). Queens Co., Rees, near Grand Lake, 46.0016°N, 65.9466°W, 29.V.2007, S. Makepeace & R. P. Webster, nest box contents of barred owl (1, RWC); Cranberry Lake P.N.A., 46.1125°N, 65.6075°W, 5–12 V.2009, R. Webster & M.-A. Giguère, mature red oak forest, Lindgren funnel trap (1, RWC).

Collection and habitat data.

Little is known about the habitat assciations of members of this genus, especially in North America (Smetana 1982). Species from the Palaearctic have been collected from hollows of trees and stumps and in litter at bases of dead trees; some species occur regularly in bird nests in hollow trees and are often observed among ants (Smetana 1982). In New Brunswick, one specimen was collected from the nest contents of a barred owl (Strix varia Barton), one from under the bark of a large, dead, fungus-covered basswood (Tilia americana L.) log, and another from a Lindgren funnel trap deployed in mature (old) red oak (Quercus rubra L.) forest. One specimen was collected in association with an ant, Formica subsericea Say, in Iowa City, Iowa (Smetana 1982). Adults were collected during May and September.

Distribution in Canada and Alaska.

ON, NB (Smetana 1988).

Map 4.

Collection localities in New Brunswick, Canada of Hypnogyra gularis.

Neohypnus beckeri Smetana, 1982**

http://species-id.net/wiki/Neohypnus_beckeri

Map 5
Material examined.

New Brunswick, Carleton Co., Jackson Falls, Bell Forest, 46.2200°N, 67.7231°W, 23–28.IV.2009, 20–26.V.2009, R. Webster & M.-A. Giguère, mature hardwood forest, Lindgren funnel traps (3, AFC). Charlotte Co., 10 km NW of New River Beach, 45.2110°N, 66.6170°W, 30.IV-17.V.2010, R. Webster & V. Webster, coll., old growth eastern white cedar forest, Lindgren funnel trap (1, AFC). Queens Co., Cranberry Lake P.N.A., 46.1125°N, 65.6075°W, 12–21.V.2009, 5–11.VI.2009, R. Webster & M.-A. Giguère, mature red oak forest, Lindgren funnel traps (2, AFC). Sunbury Co., Sunpoke Lake, 45.7665°N, 66.5545°W, 15.V.2004, R. P. Webster, red oak and maple forest, under coyote scat and in leaf litter (2, RWC); Acadia Research Forest, 46.0188°N, 66.3765°W, 14.V.2008, 18.VI.2009, R. P. Webster, mature red spruce and red maple forest, sifting leaf litter (2, AFC); Acadia Research Forest, 45.9866°N, 66.3841°W, 13–19.V.2009, 19–25.V.2009, 25.V-2.VI.2009, 2–9.VI.2009, R. Webster & M.-A. Giguère, mature (100-year-old) red spruce forest with scattered red maple and balsam fir, Lindgren funnel traps (6, AFC); ca. 5 km SE of Geary, 45.7057°N, 66.4432°W, 22.V.2009, S. Makepeace & R. Webster, in leaf litter with scat & bones under tree with active great horned owl nest (1, NBM). York Co., Charters Settlement, 45.8304°N, 66.7351°W, 18.IV.2004, 6.V.2004, R. P. Webster, mixed forest, under moist cardboard covering old chicken bones (2, RWC); same locality but 45.8395°N, 66.7391°W, 5.V.2004, 12.V.2004, 9.V.2004, R. P. Webster, mixed forest, in compost (decaying vegetables) (3, RWC); same locality but 45.8286°N, 66.7365°W, 7.VI.2005, R. P. Webster, mature red spruce and eastern white cedar forest, in leaf litter (2 , RWC); Canterbury, “Browns Mountain Fen Complex”, 45.8937°N, 67.6564°W, 8.VI.2004, D. Sabine & R. Webster, black spruce bog with eastern white cedar, in moist sphagnum on bog margin (1, RWC); 14 km WSW of Tracy, S of Rt. 645, 45.6741°N, 66.8661°W, 26.IV-10.V.2010, R. Webster & C. MacKay, coll., old mixed forest with red and white spruce, red and white pine, balsam fir, eastern white cedar, red maple, and Populus sp., Lindgren funnel traps (2, AFC).

Collection and habitat data.

In New Brunswick, adults were collected from under coyote scat, under cardboard covering old chicken bones, in compost, in leaf litter in hardwood and mixed forests, and in moist sphagnum on the margin of a black spruce and eastern white cedar bog/fen. Smetana (1982) reported most specimens from leaf litter in deciduous forests, although a few were reported from a human dung trap and from under a dead beaver. Adults were collected during April, May, and June.

Distribution in Canada and Alaska.

ON, QC, NB (Smetana 1982).

Map 5.

Collection localities in New Brunswick, Canada of Neohypnus beckeri.

Phacophallus parumpunctatus (Gyllenhal, 1827)**

http://species-id.net/wiki/Phacophallus_parumpunctatus

Map 6
Material examined.

New Brunswick, York Co., Charters Settlement, 45.8395°N, 66.7391°W, 16.X.2004, R. P. Webster, mixed forest, in compost (decaying vegetables) (1, RWC).

Collection and habitat data.

In Europe, this species is synanthropic, occurring in compost, manure, and other decaying organic material (Smetana 1982). In North America, specimens of this adventive species were collected from decaying grass clippings and from a pile of moldy wood chips and damp decaying vegetation (Smetana 1982). The single specimen from New Brunswick was collected from decaying vegetables (compost) in October.

Distribution in Canada and Alaska.

ON, QC, NB (Smetana 1982).

Map 6.

Collection localities in New Brunswick, Canada of Phacophallus parumpunctatus.

Xestolinus abdominalis Casey, 1906**

http://species-id.net/wiki/Xestolinus_abdominalis

Map 7
Material examined.

New Brunswick, Sunbury Co., Acadia Research Forest, 46.0188°N, 66.3765°W, 14.V.2007, R. P. Webster, mixed forest, in flight, collected with net (1 sex undetermined, RWC). York Co., Charters Settlement, 45.8267°N, 66.7343°W, 30.IV.2005, R. P. Webster, Carex marsh, in sphagnum hummock (1 sex undetermined, RWC).

Collection and habitat data.

Little is known about the habitat associations of this species. One of the New Brunswick specimens was collected from a sphagnum hummock in a Carex marsh, another was collected while it was flying in a mixed forest near a Carex marsh. Adults were collected in late April and May.

Distribution in Canada and Alaska.

SK, MB, ON, QC, NB (Smetana 1982).

Map 7.

Collection localities in New Brunswick, Canada of Xestolinus abdominalis.

Tribe Staphylinini Latreille, 1802 Subtribe Quediina Kraatz, 1857
Acylophorus (Amacylophorus) pratensis LeConte, 1863**

http://species-id.net/wiki/Acylophorus_pratensis

Map 8
Material examined.

New Brunswick, Carleton Co., Jackson Falls, Bell Forest, 46.2150°N, 67.7190°W, 12.VI.2008, R. P. Webster, river margin, treading vegetation in seepage area (1, NBM). Charlotte Co., 3.5 km NW of Pomeroy Ridge, 45.3087°N, 67.4362°W, 16.VI.2008, R. P. Webster, red maple swamp, in leaves and moss near small vernal pool (1, NBM). Northumberland Co., Goodfellow Brook P.N.A., 46.8943°N, 65.3796°W, 23.V.2007, R. P. Webster, old growth eastern white cedar swamp, in grass litter and moss on hummocks near pool (1 ♂, 1 sex undetermined, NBM, RWC). Restigouche Co., Jacquet River Gorge P.N.A. at Jacquet River, 47.7765°N, 66.1277°W, 13.VIII.2010, R. P. Webster, in moss on rocks in middle of river, splashing rocks (1, NBM). York Co., Charters Settlement, 45.8395°N, 66.7391°W, 23.IV.2004, 3.VI.2004, 9.V.2005, 6.X.2005, R. P. Webster, mixed forest, in litter and moss near margin of small shaded brook (5, RWC); same locality and collector but 45.8283°N, 66.7350°W, 8.V.2004, sedge marsh, in sphagnum hummock (1, RWC); same locality and collector but 45.8428°N, 66.7279°W, 23.VI.2004, 20.IV.2005, mixed forest, (shaded) margin of small sedge marsh in moist sphagnum (2, RWC); 8.4 km W of Tracy off Rt. 645, 45.6821°N, 66.7894°W, 14.V.2008, R. P. Webster, wet alder swamp, in grass hummock (1, RWC).

Collection and habitat data.

In New Brunswick, most adults were collected in red maple (Acer rubrum L.) swamps, alder (Alnus sp.) swamps, and eastern white cedar swamps, usually along vernal pool and brook margins, and in Carex marshes. One adult was collected from a seepage area along a river margin. Adults were sifted from moss and various kinds of grass and leaf litter. Elsewhere, specimens were collected from dead swamp grass and moss (Smetana 1971a), leaf litter in a cedar bog, and a pitfall trap in a bog (Smetana 1981). Adults in New Brunswick were collected in April, May, and June.

Distribution in Canada and Alaska.

ON, QC, NB, NF (Smetana 1971a, 1973, 1981).

Map 8.

Collection localities in New Brunswick, Canada of Acylophorus pratensis.

Acylophorus (Amacylophorus) caseyi Leng, 1920

http://species-id.net/wiki/Acylophorus_caseyi

Map 9
Material examined.

New Brunswick, Charlotte Co., Rt. 3 at Deadwater Brook, 45.4744°N, 67.1225°W, 3.VI.2005, R. P. Webster, forested black spruce bog, marshy stream margin, treading (1, RWC); near New River, 45.1616°N, 66.6649°W, 7.VII.2006, R. P. Webster, treading sedge marsh (1, NBM); near Clark Ridge, 45.3155°N, 67.4406°W, 27.V.2007, R. P. Webster, beaver pond, treading vegetation (1, NBM). Queens Co., Upper Gagetown, bog adjacent to Hwy 2, 45.8316°N, 66.2346°W, R. P. Webster, tamarack bog, in sphagnum hummock and litter at bog margin (1 ♂, 2 sex undetermined, NBM, RWC). York Co., Charters Settlement, 45.8267°N, 66.7343°W, 8.V.2004, 16.IV.2005, 30.IV.2005, 14.V.2005, R. P. Webster, Carex marsh in sphagnum hummocks (5, RWC).

Additional Maine Record.

Penobscot Co., T6 R8 WELS, Marble Fen, 46.1245°N, 68.6983°W, 13.VI.2003, P. deMaynadier and R. Webster, open wet tamarack bog, in moist sphagnum (treading) (1, NBM).

Collection and habitat data.

Smetana (1971a, 1976) reported this species from swampy and marshy areas, and along lake and bog margins. Adults occurred in wet moss, wet sphagnum, floating sphagnum mats, leaves and debris, and other floating vegetation. In Nova Scotia, adults were collected in a eutrophic, Typha latifolia L. marsh (Smetana 1965). In New Brunswick, this species was found in marsh vegetation or saturated sphagnum hummocks along a marshy stream margin near a forested black spruce bog, a tamarack (Larix laricina (Du Roi) Koch) bog, a beaver pond, and in Carex marshes. Most adults were collected by treading vegetation into water. Adults were collected in April, May, June, and July.

Distribution in Canada and Alaska.

ON, QC, NB, NS (Smetana 1971a, 1973, 1976). Smetana (1990) reported Acylophorus caseyi from western Maine near the border with New Hampshire (Wilsons Mills Bog, Oxford Co.). The above record from Maine represents a significant eastern range extension in the state. It is apparent from the above records that Acylophorus caseyi probably has a more continuous distribution in the Northeast and the Maritime provinces as a whole than was suggested by the collection records reported in Majka et al. (2009). These distributional gaps likely reflect incomplete collecting effort in the appropriate wetland habitats. One must use treading to collect this species from the wetland habitats that this species usually frequents.

Map 9.

Collection localities in New Brunswick, Canada and Maine, United States of America of Acylophorus caseyi.

Hemiquedius ferox (LeConte, 1878)

http://species-id.net/wiki/Hemiquedius_ferox

Map 10
Material examined.

New Brunswick, Carleton Co., Jackson Falls, 46.2257°N, 67.7420°W, 22.V.2010, R. P. Webster, river margin, in gravel near water on gravel bar (1, NBM). Charlotte Co., 3.0 km NW of Pomeroy Ridge, 45.3059°N, 67.4343°W, 5.VI.2008, R. P. Webster, alder swamp, in moss hummocks with grasses (2, NBM, RWC); near New River, 45.2118°N, 66.6179°W, 7.VII.2008, R. P. Webster, mixed forest, margin of small pond, treading Carex hummock (1, RWC). Queens Co., Grand Lake Meadows P.N.A., 45.8227°N, 66.1209°W, 24.VIII-3.IX.2010, C. Hughes & K. Burgess, old silver maple forest with green ash and seasonally flooded marsh, Lindgren funnel trap (1, AFC). Sunbury Co., Maugerville, Portobello Creek N.W.A., 45.8992°N, 66.4248°W, 27.V.2004, 5.VI.2004, R. P. Webster, silver maple swamp, margin of small vernal pond in leaf litter (2, RWC); near Sunpoke Lake, 45.7662°N, 66.5526°W, 20.VI.2007, R. P. Webster, seasonally flooded marsh, treading (1 sex undetermined, RWC). York Co., Fredericton, University of New Brunswick Woodlot, 45.9391°N, 66.6747°W, 17.VIII.2009, R. Webster, D. McAlpine, & G. Forbes, within wall of a beaver (Castor canadensis) lodge (4 ♀, RWC).

Collection and habitat data.

Hemiquedius feroxwas reported by Smetana (1971a) from various wet habitats, such as swamps, lake margins, and marshes. Adults were found in wet moss and leaves and in beaver lodges in late fall. Adults were found in similar habitats in New Brunswick, including an alder swamp, silver maple (Acer saccharinum L.) swamps, pond margins, a seasonally flooded marsh, a gravel bar on river, and a beaver lodge. Adults occurred in moss and Carex hummocks, in leaf litter along vernal pond margins and within the wall of a beaver lodge. Adults were collected by sifting litter and moss or treading vegetation into water. One individual was collected in a Lindgren funnel trap. Adults were captured during May, June, July, August, and September.

Distribution in Canada and Alaska.

ON, QC, NB, NS (Smetana 1971a). It is apparent from the above records that Hemiquedius ferox is more widely distributed in the Maritime provinces than was suggested by the collection records reported in Majka et al. (2009).

Map 10.

Collection localities in New Brunswick, Canada of Hemiquedius ferox.

Heterothops minor Smetana, 1971

http://species-id.net/wiki/Heterothops_minor

Map 11
Material examined.

New Brunswick, York Co., Upper Brockway, 45.5684°N, 67.0993°W, 23.IV.2006, R. P. Webster, forested black spruce bog, in sphagnum (1, RWC).

Collection and habitat data.

Little is known about the habitat associations of this species.Smetana (1976) reported specimens from under driftwood on a muddy river bank and from a pitfall trap on the margin of swampy pool in the Northwest Territories. The single adult from New Brunswick was sifted from sphagnum in a forested black spruce bog in late April.

Distribution in Canada and Alaska.

NT, BC, AB, MB, ON, QC, NB, NS, NF (Smetana 1971a, 1973, 1976, 1981).

Map 11.

Collection localities in New Brunswick, Canada of Heterothops minor.

Heterothops pusio LeConte, 1863**

http://species-id.net/wiki/Heterothops_pusio

Map 12
Material examined.

New Brunswick, Carleton Co., Jackson Falls, Bell Forest, 46.2152°N, 67.7190°W, 1.VI.2005, M.-A. Giguère & R. Webster, river margin, flying adults collected with aerial net between 16:00 and 18:00 h (1 ♂, 1 ♀, RWC). Restigouche Co., Jacquet River Gorge P.N.A., 47.8197°N, 66.0835°W, 23.VI.2008, R. P. Webster, river margin, among cobblestones (1, NBM). York Co., Charters Settlement, 45.8395°N, 66.7391°W, 10.VI.2006, R. P. Webster, mixed forest, m.v. light (3, RWC); same locality data, collector, and forest type, 26.V.2008, compost (decaying vegetables) (1, RWC).

Collection and habitat data.

Smetana (1971a) reported this species from compost and grass piles, leaf and ground litter, and from old deserted beaver lodges. In New Brunswick, adults were sifted from compost and among cobblestones along a river margin. Other individuals were collected at a mercury-vapor light and during a late afternoon aerial flight. Adults were collected in May and June.

Distribution in Canada and Alaska.

BC, ON, QC, NB (Smetana 1971a, 1973, 1981).

Map 12.

Collection localities in New Brunswick, Canada of Heterothops pusio.

Quedius (Microsaurus) campbelli Smetana, 1971**

http://species-id.net/wiki/Quedius_campbelli

Map 13
Material examined.

New Brunswick, Restigouche, Co., Dionne Brook P.N.A., 47.9064°N, 68.3441°W, 31.V-15.VI.2011, M. Roy & V. Webster, old-growth white spruce and balsam fir forest, Lindgren funnel trap (1 ♀, RWC). York Co., Fredericton, University of New Brunswick Woodlot, 45.9391°N, 66.6747°W, 17.VIII.2009, R. P. Webster, D. McAlpine, & G. Forbes, in beaver (Castor canadensis) lodge, within wall of lodge (2 ♂, NBM, RWC).

Collection and habitat data.

Smetana (1971a, 1976) reported specimens from near or within (in walls) muskrat nests and beaver lodges. Two of the New Brunswick specimens were collected from within the wall of a beaver lodge in August. One was captured during June in a Lindgren funnel trap deployed in an old balsam fir (Abies balsamea (L.) Mill.) and white spruce (Picea glauca (Moench) Voss) forest.

Distribution in Canada and Alaska.

ON, QC, NB (Smetana 1971a, 1976).

Map 13.

Collection localities in New Brunswick, Canada of Quedius campbelli.

Quedius (Microsaurus) canadensis (Casey, 1915)

http://species-id.net/wiki/Quedius_canadensis

Map 14
Material examined.

Additional New Brunswick records. Carleton Co., Jackson Falls, Bell Forest, 46.2200°N, 67.7231°W, 18.IX.2006, R. P. Webster, mature hardwood forest, under bark of large, dead, standing basswood covered with bracket fungi (1 ♂, RWC); same locality, 4–12.VI.2008, 12–19.VI.2008, 5–12.VII.2008, 23–28.IV.2009, 9–14.V.2009, 14–20.V.2009, 9–16.VI.2009, R. Webster & M.-A. Giguère, mature hardwood forest, Lindgren funnel traps (2 ♂, 3 ♀, 6 sex undetermined, AFC, NBM, RWC). Charlotte Co., 10 km NW of New River Beach, 45.2110°N, 66.6170°W, 30.IV-17.V.2010, R. P. Webster & V. Webster, coll., old-growth eastern white cedar forest, Lindgren funnel trap (1, AFC). Queens Co., Cranberry Lake P.N.A., 46.1125°N, 65.6075°W, 24.IV-5 V.2009, R. Webster & M.-A. Giguère, mature red oak forest, Lindgren funnel traps (5, AFC, NBM). Restigouche Co., Jacquet River Gorge P.N.A., 47.8160°N, 66.0083°W, 14.VIII.2010, R. P. Webster, old eastern white cedar forest, in polypore fungi on Populus log (1, NBM); Dionne Brook P.N.A., 47.9030°N, 68.3503°W, 28.VII-9.VIII.2011, 9–23.VIII.2011, M. Roy & V. Webster, old-growth northern hardwood forest, Lindgren funnel trap (2, NBM); same locality and collectors but 47.9064°N, 68.3441°W, 27.VI-14.VII.2011, 9–23.VIII.2011, old-growth white spruce and balsam fir forest, Lindgren funnel traps (2, AFC, NBM). Sunbury Co., Acadia Research Forest, 45.9866°N, 66.3841°W, 28.IV-8.V.2009, 8–13.V.2009, 13–19.V.2009, 2–9.VI.2009, 29.VII-4.VIII.2009, R. Webster & M.-A. Giguère, mature (110 year-old) red spruce forest with scattered red maple and balsam fir, Lindgren funnel traps (1 ♂, 13 sex undetermined, AFC, RWC). York Co., Charters Settlement, 45.8395°N, 66.7391°W, 25–29.IV.2008, R. P. Webster, mixed forest, Lindgren funnel trap (1 ♂, RWC); 15 km W of Tracy, off Rt. 645, 45.6848°N, 66.8821°W, 25.IV-4V.2009, 4–11.V.2009, 11–19.V.2009, R. Webster & M.-A. Giguère, mature (120–180 year-old) red pine forest, Lindgren funnel traps (3 ♂, 4 sex undetermined, AFC, RWC); 14 km WSW of Tracy, S of Rt. 645, 45.6741°N, 66.8661°W, 26.IV-10.V.2010, R. Webster & C. MacKay, coll., old mixed forest with red and white spruce, red and white pine, balsam fir, eastern white cedar, red maple, and Populus sp., Lindgren funnel traps (2, AFC).

Collection and habitat data.

Little is known about the habitat associations of this species. Smetana (1973) reported a specimen from Polyporus betulinus (Bull.) Fr. In New Brunswick, one specimen was collected from under bark of a large, dead, standing basswood covered with bracket fungi (polypore fungi), one from under bark of a spruce log, and another in a polypore fungi on a Populus log. Many specimens were captured in Lindgren funnel traps deployed in a variety of forest types, including an old red pine (Pinus resinosa Ait.) forest, a hardwood with sugar maple (Acer saccharum Marsh.) and American beech (Fagus grandifolia Ehrh.), an old-growth northern hardwood forest, a red spruce forest, an old-growth white spruce and balsam fir forest, a mixed forest, and an old eastern white cedar forest. These traps mimic tree trunks (Lindgren 1983), and it is possible that this species lives in microhabitats associated with standing trees. Adults were collected in April, May, June, July, August, and September.

Distribution in Canada and Alaska.

ON, QC, NB, NS (Smetana 1971a, 1973, 1978; Bishop et al. 2009). This species was previously known in New Brunswick from one specimen collected in Dalhousie during 1925 by Johansen (Smetana 1971a).

Map 14.

Collection localities in New Brunswick, Canada of Quedius canadensis.

Quedius (Microsaurus) criddlei (Casey, 1915)**

http://species-id.net/wiki/Quedius_criddlei

Map 15
Material examined.

New Brunswick, Queens Co., Cranberry Lake P.N.A., 46.1125°N, 65.6075°W, 7–13.VII.2011, 20.VII-4.VIII.2011, M. Roy & V. Webster, old red oak forest, Lindgren funnel trap (2 ♀, NBM, RWC). Restigouche Co., Dionne Brook P.N.A., 47.9030°N, 68.3503°W, 27.VI-14.VII.2011, 9–23.VIII.2011, M. Roy & V. Webster, old-growth northern hardwood forest, Lindgren funnel traps (2 ♂, 2 ♀, NBM, RWC); same locality and collectors but 47.9064°N, 68.3441°W, 31.V-15.VI.2011, 15–27.VI.2011, 27.VI-14.VII.2011, 14–28.VII.2011, 9–23.VIII.2011, old-growth white spruce and balsam fir forest, Lindgren funnel traps (3 ♂, 6 ♀, AFC, NBM, RWC). York Co., 15 km W of Tracy off Rt. 645, 45.6848°N, 66.8821°W, 1–8.VI.2009, R. Webster & M.-A. Giguère, old red pine forest, Lindgren funnel trap (1 ♀, RWC); same locality and habitat data, 4–16.VI.2010, R. Webster & C. MacKay, Lindgren funnel traps (1 ♂, RWC). Quebec, Saguenay Co. Sept-Iles, 20.V.1985, 13.IX.1985, C. Chantal (1♂, 1 ♀, CCC).

Collection and habitat data.

Little is known about the habitat associations of this species. Adults have been taken from leaf litter in Larix forests, in rotten Douglas-fir (Pseudotsuga taxifolia Britton) and grand fir (Abies grandis (Douglas ex. D. Don) Lindl.) logs, under board in a meadow, ex fungus, and in association with the ant Formica neorufibarbis Emery (probably accidentally) (Smetana 1971a). The New Brunswick specimens were collected in Lindgren funnel traps deployed in an old (120- to 180-year-old trees) red pine forest, an old red oak forest, an old-growth northern hardwood forest, and an old-growth white spruce and balsam fir forest. Adults were collected during May, June, July, August, and September in New Brunswick and Quebec.

Distribution in Canada and Alaska.

NT, YT, BC, AB, MB, ON, QC, NB (Smetana 1971a, 1990). The records from Quebec and New Brunswick represent significant range extensions east of the known distribution of this species reported by Smetana (1971a, 1990), indicating that this species is transcontinental in distribution in Canada.

Map 16.

Collection localities in New Brunswick, Canada of Quedius erythrogaster.

Quedius (Microsaurus) erythrogaster Mannerheim, 1852

http://species-id.net/wiki/Quedius_erythrogaster

Map 16
Material examined.

Additional New Brunswick records, Carleton Co., Jackson Falls, Bell Forest, 46.2208°N, 67.7211°W, 10.IV.2005, R. P. Webster, mature hardwood forest, in leaf litter at base of tree (1 ♂, RWC). Queens Co., Cranberry Lake P.N.A., 46.1125°N, 65.6075°W, 24.IV–5 V.2009, 5–12 V.2009, R. Webster & M.-A. Giguère, mature red oak forest, Lindgren funnel traps (2, AFC). Restigouche Co., Dionne Brook P.N.A., 47.9030°N, 68.3503°W, 27.VI–14.VII.2011, M. Roy & V. Webster, old-growth northern hardwood forest, Lindgren funnel traps (1 ♂, 2 ♀, NBM, RWC). Sunbury Co., Noonan, 45.9923°N, 66.4099°W, 22.VI.2007, S. Makepeace & R. Webster, mature mixed forest, in nest contents of barred owl, 7 m high in cavity in a red maple (1 ♂, 1 ♀, RWC); Acadia Research Forest, 45.9866°N, 66.3841°W, 22–25.IV.2009, 25.IV-4.V.2009, 4–11.V.2009, 19–25.V.2009, R. Webster & M.-A. Giguère, mature (110-year-old) red spruce forest with scattered red maple and balsam fir, Lindgren funnel traps (4, AFC). York Co., Charters Settlement, 45.8395°N, 66.7391°W, 18.IV.2004, 30.IV.2004, 5.V.2006, 9.V.2006, R. P. Webster, mixed forest, in compost (decaying vegetables) (2 ♂, 2 ♀, RWC); same locality but 45.8430°N, 66.7275°W, 6.X.2005, R. P. Webster, regenerating mixed forest, baited with pile of decaying mushrooms (2 ♂, RWC); 15 km W of Tracy off Rt. 645, 45.6848°N, 66.8821°W, 22–25.IV.2009, 25.IV–4.V.2009, 4–11.V.2009, 19–25.V.2009, R. Webster & M.-A. Giguère, Lindgren funnel traps (4, AFC).

Collection and habitat data.

Quedius erythrogastertypically lives in nests and burrows of various mammals and in caves but has been found in decaying organic matter and debris (Smetana 1971a), including wet leaf litter (Smetana 1976). In New Brunswick, adults were found in leaf litter early in the season when snow was still present (possibly an overwinter site), compost (decaying vegetables), and decaying mushrooms. Other adults were collected from the nest contents of a barred owl in a tree hole, suggesting this species may also live in association with tree-cavity-nesting birds. Adults were also captured in Lindgren funnels traps deployed in an old red oak forest, an old red pine forest, and an old-growth northern hardwood forest. Adults were collected in April, May, June, July, and October.

Distribution in Canada and Alaska.

BC, AB, SK, ON, QC, NB (Smetana 1971a, 1973, 1976, 1981). Quedius erythrogaster was listed as occurring in New Brunswick by Majka et al. (2011) without any supporting references or data. Here, we provide the first documented records from New Brunswick.

Map 15.

Collection localities in New Brunswick and Quebec, Canada of Quedius criddlei.

Quedius (Microsaurus) mesomelinus (Marsham, 1802)

http://species-id.net/wiki/Quedius_mesomelinus

Map 17
Material examined.

Additional New Brunswick records, Carleton Co., Jackson Falls, Bell Forest, 46.2200°N, 67.7231°W, 18.IX.2006, 9.X.2006, R. P. Webster, mature hardwood forest, under bark of large dead standing basswood covered with bracket fungi (1 ♂, 1 ♀, RWC); same locality, 4–12.VI.2008, 12–19.VI.2008, 19–27.VI.2008, 5–12.VII.2008, 12–19.VII.2008, 19–28.VII.2008, R. P. Webster, mature hardwood forest, Lindgren funnel traps (2 ♂, 4 ♀, 7 sex undetermined, AFC, RWC); same locality, 14–20.V.2009, 16–21.VI.2009 , R. Webster & M.-A. Giguère, mature hardwood forest, Lindgren funnel traps (2, AFC). Restigouche, Co., Dionne Brook P.N.A., 47.9064°N, 68.3441°W, 27.VI-14.VII.2011, M. Roy & V. Webster, old-growth white spruce and balsam fir forest, Lindgren funnel trap (1, NBM). York Co., Odell Park, 45.9570°N, 66.6695°W, 19.VI.2005, R. P. Webster, moist wood chips and decaying plant material (1 ♀, RWC).

Collection and habitat data.

In Europe, this species is typically found in synanthropic situations in decaying organic materials such as compost (Smetana 1971a). It has also been reported from mammal burrows, tree holes, and caves in natural settings. In New Brunswick, adults were collected from under bark of a fungus-covered, dead, standing basswood, among moist wood chips and decaying plant material, and from Lindgren funnel traps deployed in a hardwood forest and an old-growth white spruce and balsam fir forest. Adults were captured in June, July, September, and October.

Distribution in Canada and Alaska.

AK, BC, AB, MB, ON, QC, NB, NS, NF (Smetana 1971a; Majka and Smetana 2007). This adventive species was first reported from New Brunswick by Majka and Smetana (2007) from specimens collected in Saint John in 1907 by G. Morrisey.

Map 17.

Collection localities in New Brunswick, Canada of Quedius mesomelinus.

Quedius (Microsaurus) peregrinus Gravenhorst, 1806

http://species-id.net/wiki/Quedius_peregrinus

Map 18
Material examined.

Additional New Brunswick records. Albert Co., Caledonia Gorge P.N.A., 45.8257°N, 64.7791°W, 6.VII.2011, R. P. Webster, old hardwood forest (sugar maple and beech), in decayed fleshy polypore in log (1 ♂, NBM). Sunbury Co., Maugerville, Portobello Creek N.W.A., 45.9031°N, 66.4268°W, 11.IX.2006, R. P. Webster, red oak and red maple forest, on gilled mushroom (1 ♀, RWC); Acadia Research Forest, pitfall trap (collection) dates, 17.VIII.1999, 24.VIII.1999, 25.VIII.1999, 8.IX.1999, 13.IX.1999, 15.IX.1999, G. Gesner, strip, select., and control plots (15, AFC); same locality but 46.0188°N, 66.3765°W, 17.VIII.2007, R. P. Webster, mature red spruce and red maple forest, sifting moss (1, AFC); same locality and collector but 46.0173°N, 66.3741°W, 18.IX.2007, 8.5 year-old regenerating mixed forest, in sphagnum and leaf litter at bottom of old tire depression (1, AFC). York Co., Charters Settlement, 45.8395°N, 66.7391°W, 18.VII.2006, R. P. Webster, mixed forest, on rotting fungus covered log (1 ♀, RWC); same locality data, collector, and (adjacent) forest type, 4.X.2005, residential lawn, on soil at base of grasses (1 ♂, RWC); same locality, collector, and adjacent forest type but 45.8348°N, 66.7335°W, 4.VIII.2004, in fleshy fungi (1, NBM); same locality and collector but 45.8430°N, 66.7275°W, 12.VII.2005, regenerating mixed forest, beating foliage (2 ♂, 3 ♀, RWC); same locality data, collector, and forest type, 25.IX.2005, baited with pile of decaying mushrooms (1 ♂, RWC).

Collection and habitat data.

One of the Nova Scotia specimens was collected by treading wet Sphagnum (Smetana 1973), otherwise little is known about the habitat associations of this species (Smetana 1971a). Specimens from New Brunswick were collected in red oak and red maple forests, a red spruce and red maple forest, an old sugar maple and American beech forest, and regenerating mixed forests. Adults were collected from gilled mushrooms, a decayed fleshy polypore fungus on a log, from a rotten fungus-covered log, baited with decaying mushrooms, sifted from sphagnum and leaf litter at bottom of old tire depression, and swept from foliage in a regenerating forest. Adults were also captured in pitfall traps in large numbers (Klimaszewski et al. 2005). This species is probably associated with decaying organic matter, such as decaying mushrooms. Adults were captured during July, August, September, and October.

Distribution in Canada and Alaska.

ON, QC, NB, NS (Smetana 1971a, 1973; Klimaszewski et al. 2005). This species was first reported from New Brunswick by Klimaszewski et al. (2005) from specimens collected in pitfall traps at the Acadia Research Forest (Sunbury Co.)

Map 18.

Collection localities in New Brunswick, Canada of Quedius peregrinus.

Quedius (Quedius) curtipennis Bernhauer, 1908

http://species-id.net/wiki/Quedius_curtipennis

Map 19
Material examined.

Additional New Brunswick records. Carleton Co., Jackson Falls, Bell Forest, 46.2152°N, 67.7190°W, 21.VIII.2004, 15.IX.2004, R. P. Webster, upper river margin under litter on clay soil (2 ♀, RWC); Hovey Hill P.N.A., 46.1115°N, 67.7770°W, 10.V.2005, R. P. Webster, mature hardwood forest in moist leaf litter and moss on margin of vernal pond (2 ♂, 1♀, RWC). York Co., Pokiok, 2.VI.1995, (G. Gesner) pitfall trap (1♂, AFC); Charters Settlement, 45.8395°N, 66.7391°W, 30.IV.2005, R. P. Webster, mixed forest, in compost (decaying vegetables) (1 ♂, RWC); same locality data, collector, and forest type, 5.IX.2006, in pile of decaying corncobs and cornhusks (1♀, RWC).

Collection and habitat data.

This species has been reported mostly from around human settlements in various kinds of debris and under stones (Smetana (1971a). Adults have also been found in natural habitats in moss and leaf litter (Smetana 1971a, 1978). In New Brunswick, adults were collected in natural habitats (river margin in litter, in moist leaf litter and moss on vernal pond margin in a hardwood forest) and in synanthropic situations (in compost and pile of decaying corncobs and cornhusks near a home). Adults were collected in April, May, June, August, and September.

Distribution in Canada and Alaska.

BC, ON, NB, NS (Smetana 1971a; Majka and Smetana 2007; Brunke and Marshall 2011). This adventive species was first reported from New Brunswick and Nova Scotia (and eastern North America) by Majka and Smetana (2007). An earlier record (Truro, 1984) from Nova Scotia was later reported by Majka and Klimaszewski (2008a). The record from New Brunswick was based on a specimen collected by CG Majka at Mary’s Point in 2002.

Map 19.

Collection localities in New Brunswick, Canada of Quedius curtipennis.

Quedius (Quedius) labradorensis labradorensis Smetana, 1965

http://species-id.net/wiki/Quedius_labradorensis_labradorensis

Map 20
Material examined.

Additional New Brunswick records, Restigouche Co., Little Tobique River near Red Brook, 47.4462°N, 67.0689°W, 24.V.2007, R. P. Webster, coll., old growth eastern white cedar forest, in moss and leaf litter near brook (1 ♂, NBM); MacFarlane Brook P.N.A., 47.6018°N, 67.6263°W, 25.V.2007, R. P. Webster, old growth eastern white cedar swamp, in moss near brook (1 ♂, RWC); Berry Brook P.N.A., 47.8140°N, 66.7578°W, 26.V.2007, R. P. Webster, old growth eastern white cedar swamp, in moss on hummock at base of eastern white cedar (2 ♀, RWC). Saint John Co., Musquash, 45.1696°N, 66.3140°W, 7.V.2006, R. P. Webster, spruce forest, in sphagnum and litter on margin of brook (1 ♂, RWC); ca. 2.0 km NE of Maces Bay, 45.1168°N, 66.4552°W, 8.V.2006, R. P. Webster, eastern white cedar swamp, under deer dung (1 ♂, RWC). York Co., Charters Settlement, 45.8395°N, 66.7391°W, 30.IV.2004, R. P. Webster, mixed forest, m.v. light (1 ♀, RWC).

Collection and habitat data.

Smetana (1976) reported this species from moss, mushrooms, and deciduous leaf litter (birch and poplar stands) near streams. In the Alberta foothills forests, Quedius labradorensis was considered to be an open-ground specialist after forest harvesting and only extended a short distance into adjacent uncut forests (Pohl et al. (2007). Numbers of this species also increased after harvesting. In New Brunswick, most adults were found in old-growth eastern white cedar swamps in moss usually near small streams. One adult was found under white-tailed deer (Odocoileus virginianus (Zimmerman)) dung, and another was collected at a mercury-vapor light. Adults were collected during April and May.

Distribution in Canada and Alaska.

AK, BC, NT, AB, MB, ON, QC, NB, NF (Smetana 1971a, 1973, 1976, 1978). Majka et al. (2011) listed this species as occurring in New Brunswick without any supporting references or data. Here, we provide the first documented records from New Brunswick.

Map 20.

Collection localities in New Brunswick, Canada of Quedius l. labradorensis.

Quedius (Quedionuchus) plagiatus Mannerheim, 1843

http://species-id.net/wiki/Quedius_plagiatus

Map 21
Material examined.

Additional New Brunswick records, Albert Co., Caledonia Gorge P.N.A., 45.8257°N, 64.7791°W, 6.VII.2011, R. P. Webster, old hardwood forest (sugar maple and beech), under bark of sugar maple log (1, NBM). Carleton Co., Hovey Hill P.N.A., 46.1115°N, 67.7770°W, 19.VIII.2004, R. P. Webster, hardwood forest, under bark of log (1 ♀, RWC); Jackson Falls, Bell Forest, 46.2200°N, 67.7231°W, 4–12.VI.2008, R. P. Webster, mature hardwood forest, Lindgren funnel trap (1, AFC); same locality, 14–20.V.2009, 16–21.VI.2009 , R. P. Webster & M.-A. Giguère, mature hardwood forest, Lindgren funnel traps (2, AFC). Charlotte Co., 5.1 km NW of Pomeroy Ridge, 45.3055°N, 67.4340°W, 5.VI.2008, R. P. Webster, mixed forest, under bark of spruce log (1, NBM); 10 km NW of New River Beach, 45.2110°N, 66.6170°W, 30.IV-17.V.2010, R. Webster & V. Webster, coll., old growth eastern white cedar forest, Lindgren funnel trap (1, AFC). Queens Co., Cranberry Lake P.N.A., 46.1125°N, 65.6075°W, 24.IV-5 V.2009, 21–27.V.2009, 5–11.VI.2009, 18–25.VI.2009, 25.VI-1 VII.2009, 21–28.VII.2009, 6–14.VIII.2009, R. Webster & M.-A. Giguère, mature red oak forest, Lindgren funnel traps (2 ♀, 13 sex undetermined, AFC, NBM, RWC). Restigouche Co., Little Tobique River near Red Brook, 47.4462°N, 67.0689°W, 24.V.2007, R. P. Webster, old-growth eastern white cedar forest, under bark of large fallen spruce (1 ♀, NBM); Jacquet River Gorge P.N.A., 47.8200°N, 66.0015°W, 13.V.2010, R. P. Webster (1, NBM); same locality but 47.8257°N, 66.0779°W, 14.V.2010, P. Giasson, old mixed forest, under bark of Populus sp. log (1, NBM); South Branch Rd., 494 m elev., 47.8767°N, 68.2657°W, 22.VI.2010, R. P. Webster, Spruce and balsam fir forest, under bark of spruce (1, NBM); Dionne Brook P.N.A., 47.9030°N, 68.3503°W, 28.VII-9.VIII.2011, M. Roy & V. Webster, old-growth northern hardwood forest, Lindgren funnel trap (2, AFC, NBM); same locality and collectors but 47.9064°N, 68.3441°W, 15–27.VI.2011, old-growth white spruce and balsam fir forest, Lindgren funnel traps (2, AFC, NBM). Sunbury Co., Acadia Research Forest, 45.9866°N, 66.3841°W, 6–24.VI.2009, 13–21.VII.2009, 21–29.VII.2009, 29.VII-4.VIII.2009, R. Webster & M.-A. Giguère, mature (100 year-old) red spruce forest with scattered red maple and balsam fir, Lindgren funnel trap (4, AFC). York Co., Charters Settlement, 45.8188°N, 66.7460°W, 25.VIII.2004, R. P. Webster, clear-cut, under bark of conifer stump (3 ♂, 3 ♀, RWC); same locality but, 45.8380°N, 66.7310°W, 14.V.2004, R. P. Webster, mixed forest, under bark of conifer (1 ♀, RWC); 15 km W of Tracy, off Rt. 645, 45.6848°N, 66.8821°W, 8–15.VI.2009, 21–28.VI.2009, R. Webster & M.-A. Giguère, mature (120–180 year-old) red pine forest, Lindgren funnel traps (4, AFC); 14 km WSW of Tracy, S of Rt. 645, 45.6741°N, 66.8661°W, 26.IV-10.V.2010, R. Webster & C. MacKay, old mixed forest with red and white spruce, red and white pine, balsam fir, eastern white cedar, red maple, and Populus sp., Lindgren funnel trap (1, AFC).

Collection and habitat data.

This common Holarctic species is found under bark of dead trees, usually coniferous species (Smetana 1971a). In New Brunswick, most specimens were found under bark of conifer logs or stumps and some under bark of hardwoods. Adults were also commonly captured in Lindgren funnel traps. Adults were collected in April, May, June, July, and August.

Distribution in Canada and Alaska.

AK, YT, NT, BC, AB, SK, MB, ON, QC, NB, NS (Smetana 1971a; Bishop et al. 2009). Quedius plagiatus was listed as occurring in New Brunswick by Majka et al. (2011) without any supporting references or data. Here, we provide the first documented records from New Brunswick.

Map 21.

Collection localities in New Brunswick, Canada of Quedius plagiatus.

Quedius (Distichalius) capucinus (Gravenhorst, 1806)

http://species-id.net/wiki/Quedius_capucinus

Map 22
Material examined.

New Brunswick, Queens Co., Cranberry Lake P.N.A., 46.1125°N, 65.6075°W, 10–11.VII.2009, R. Webster & M.-A. Giguère, mature red oak forest, u.v. light (2 ♂, 1 ♀, AFC). Restigouche Co., Dionne Brook P.N.A., 47.9030°N, 68.3503°W, 14–28.VII.2011, 28.VII-9.VIII.2011, M. Roy & V. Webster, old-growth northern hardwood forest, Lindgren funnel traps (2, AFC, NBM). York Co., Charters Settlement, 45.8430°N, 66.7275°W, 14.IX.2004, 17.IX.2004, 25.IX.2004, 6.X.2005, R. P. Webster, regenerating mixed forest, baited with pile of decaying mushrooms (1 ♂, 5 ♀, NBM, RWC); same locality but 45.8286°N, 66.7365°W, 24.VI.2006, R. P. Webster, mature mixed forest, in gilled mushroom (1 ♂, RWC); same locality but 45.8395°N, 66.7391°W, 28.IX.2006, 29.VIII.2007, R. P. Webster, mixed forest, in pile of corncobs and cornhusks (1 ♂, 1 ♀, RWC).

Collection and habitat data.

This species appears to prefer decaying organic substances and has been found on carrion, under human feces (Smetana 1971a), and in fleshy fungi (Blatchley 1910). In New Brunswick, most specimens were found in decaying mushrooms and compost (pile of corncobs and cornhusks). Two individuals were captured in Lindgren funnel traps deployed in an old-growth northern hardwood forest. Adults were found in April, June, July, August, September, and October.

Distribution in Canada and Alaska.

ON, QC, NB, NS (Smetana 1971a; Bishop et al. 2009).

Map 22.

Collection localities in New Brunswick, Canada of Quedius capucinus.

Quedius (Distichalius) cinctus (Paykull, 1790)

http://species-id.net/wiki/Quedius_cinctus

Map 23
Material examined.

Additional New Brunswick records. Restigouche Co., Mount Atkinson, 447 m elev., 47.8192°N, 68.2618°W, 21.VII.2010, R. P. Webster, spruce and balsam fir forest (boreal forest), small shaded spring-fed brook with mossy margin, in wet moss (1 ♂, RWC). York Co., Charters Settlement, 45.8430°N, 66.7275°W, 8.X.2004, 6.X.2005, R. P. Webster, regenerating mixed forest, baited with pile of decaying mushrooms (1 ♂, 3 ♀, NBM, RWC); Charters Settlement, 45.8395°N, 66.7391°W, 18.X.2004, 6.IX.2005, 5.VIII.2005, 29.III.2006, 17.IX.2006, 26.IX.2007, R. P. Webster, mixed forest, in pile of decaying (moldy) corncobs and cornhusks (4 ♂, 3 ♀, NBM, RWC); same locality data and collector but 17.IX.2006, mixed forest, in pile of decaying leaves (1 ♂, RWC).

Collection and habitat data.

In Europe, Quedius cinctususually occurs in decaying organic material, usually near human settlements (Smetana 1971a). In New Brunswick, specimens were similarly found in decaying organic material (decaying mushrooms, decaying corncobs and cornhusks, decaying leaves). One individual was found in wet moss along a cold, shaded brook. Adults were collected in April, July, September, and October.

Distribution in Canada and Alaska.

ON, NB (Majka et al. 2009; Brunke and Marshall 2011). This adventive species was first reported from New Brunswick and Canada by Majka et al. (2009) from three specimens collected from a domestic pig carcass in Bouctouche (Kent Co.) in 2007. This species is probably well established in New Brunswick and likely occurs in the intervening areas between this province and Massachusetts (Framingham and Fall River, USA), where the species was first reported by Smetana (1971a) from North America.

Map 23.

Collection localities in New Brunswick, Canada of Quedius cinctus.

Quedius (Raphirus) frigidus Smetana, 1971**

http://species-id.net/wiki/Quedius_frigidus

Map 24
Material examined.

New Brunswick, Restigouche Co., Berry Brook P.N.A., 47.8140°N, 66.7578°W, 26.V.2007, R. P. Webster, old-growth eastern white cedar forest in moss and leaf litter near brook (4 ♂, 4 ♀, NBM, RWC); MacFarlane Brook P.N.A., 47.6018°N, 67.6263°W, 25.V.2007, R. P. Webster, old growth eastern white cedar forest in moss near brook (4 ♂, NBM, RWC); Mount Atkinson, 447 m elev., 47.8192°N, 68.2618°W, 23.VI.2010, R. P. Webster, spruce and balsam fir forest (boreal forest), small, shaded, spring-fed brook with mossy margin, in wet moss (1 ♂, RWC).

Collection and habitat data.

Relatively little was previously known about the habitat requirements of this species, although it appears that this species may be associated with moss and leaf litter near small streams and other wetlands. Smetana (1973, 1976) reported the species from leaf litter in a sphagnum bog, wet sphagnum (treading) along the margin of a large spring, and in leaf litter (sifting) along a small stream. In the Alberta Foothills forests, Quedius frigidus was considered to be a mature forest specialist (Pohl et al. 2007). Adults at the three New Brunswick localities were found in moss and leaf litter near brooks in old-growth eastern white cedar forests and a mature spruce and balsam fir forest on the north-facing slope of a hill. Adults were collected during May and June.

Distribution in Canada and Alaska.

AK, NT, ON, NB, NF (Smetana 1973, 1976, 1978, 1981). Smetana (1971a, 1973) suggested that Quedius frigidus was a northern transcontinental species with glacial relic populations in southern areas at higher mountain elevations. The New Brunswick records indicate a more southerly distribution at low elevations in eastern Canada.

Map 24.

Collection localities in New Brunswick, Canada of Quedius frigidus.

Quedius (Raphirus) fulvicollis (Stephens, 1833)**

http://species-id.net/wiki/Quedius_fulvicollis

Map 25
Material examined.

New Brunswick, Albert Co., Caledonia Gorge P.N.A., 45.8176°N, 64.7800°W, 6.VII.2011, R. P. Webster, old hardwood forest (sugar maple and beech), in mossy seepage area with Carex, sifting moss and grass litter (2 ♂, 1♀, NBM, RWC). Restigouche Co., 7.5 km S of Saint Arthur, 47.8283°N, 66.7654°W, 14.VI.2006, R. P. Webster, old-growth eastern white cedar forest, in moist leaves at base of large white birch (1 ♂, RWC). York Co., Charters Settlement, 45.8395°N, 66.7391°W, 19.V.2005, R. P. Webster, alder swamp, in moist leaf litter near small (slow flowing) brook (1 ♂, RWC); Mazerolle Settlement, 45.8717°N, 66.8273°W, 28.IV.2006, R. P. Webster, eastern white cedar swamp, in moss and leaf litter near brook (1 ♀, RWC); 8 km NW of Magundy, 45.8712°N, 67.2221°W, 8.VII.2006, R. P. Webster, mature hardwood forest, margin of small cold (spring-fed) brook among sedges (1 ♂, 2 ♀, RWC).

Collection and habitat data.

Adults of this species occur in moist moss, sphagnum, deciduous leaf litter, and mixed forest litter in various wet biotypes such as small stream margins, lake margins, and wet areas in forests (Smetana 1971a, 1973, 1976). In New Brunswick, most specimens were found in moist leaf litter, moss, or among sedges near small brooks in alder swamps, eastern white cedar forests, and hardwood forests. Adults were collected during April, May, June, and July.

Distribution in Canada and Alaska.

AK, YT, BC, AB, MB, ON, QC, NB, NF (Smetana 1971a, 1973, 1976).

Map 26.

Collection localities in New Brunswick, Canada of Quedius simulator.

Quedius (Raphirus) simulator Smetana, 1971**

http://species-id.net/wiki/Quedius_simulator

Map 26
Material examined.

New Brunswick, Restigouche Co., Mount Atkinson, 447 m elev., 47.8192°N, 68.2618°W, 21.VII.2010, R. P. Webster, spruce and balsam fir forest (boreal forest), small, shaded, spring-fed brook with mossy margin, in wet moss (1 ♂, RWC); Jacquet River Gorge P.N.A., 47.8109°N, 66.0905°W, 13.VIII.2010, R. P. Webster, old mixed forest, small shaded spring-fed brook with mossy margin, in wet moss (1 ♂, 2 ♀, RWC).

Collection and habitat data.

This species was reported from very wet debris and moss in small gullies and depressions on the forest floor and edges of oligotrophic ponds in mixed forests, and from Carex hummocks and wet debris from various wet habitats such as lake margins, swamps, and marshes (Smetana 1971, 1973). Specimens from Moosonee, Ontario were collected by sifting leaf litter under willow (Salix sp.) and alder bushes near the Moose River (Smetana 1976). In New Brunswick, adults were found in wet moss along shaded, cold, spring-fed brooks. Adults were collected during July and August.

Distribution in Canada and Alaska.

AK, NT, BC, AB, SK, MB, ON, QC, NB, LB (Smetana 1971a, 1973, 1976, 1981, 1990). This is a northern transcontinental species, with most records from the boreal forest of northern Canada (Smetana 1971a, 1973, 1976, 1981).

Map 25.

Collection localities in New Brunswick, Canada of Quedius fulvicollis.

Subtribe Staphylinina Latreille, 1802
Staphylinus ornaticauda LeConte, 1863

http://species-id.net/wiki/Staphylinus_ornaticauda

Map 27
Material examined.

New Brunswick, Charlotte Co., 3 km SW of King Brook Lake, 45.3194°N, 67.4414°W, 27.V.2007, R. P. Webster, eastern white cedar, red maple, and black ash swamp, in moist litter and moss near small pools with Carex (2 ♂, 1 ♀, RWC); 3.5 km NW of Pomeroy Ridge, 45.3087°N, 67.4362°W, 5.VI.2008, 16.VI.2008, R. P. Webster, red maple swamp, in leaves and moss near small vernal pool with Carex (1 ♂, 2 ♀, NBM). Northumberland Co., Goodfellow Brook P.N.A., 46.8943°N, 65.3796°W, 23.V.2007, R. P. Webster, old-growth eastern white cedar swamp, in moss and litter on hummock (2 ♂, RWC). York Co., Canterbury, “Browns Mountain Fen”, 45.8967°N, 67.6343°W, 2.V.2005, 29.IV.2006, M.-A. Giguère & R. P. Webster, eastern white cedar swamp, in litter at base of cedar (2 ♂, RWC); same locality but 45.8957°N, 67.6462°W, 29.IV.2006, R. P. Webster, eastern white cedar swamp in sphagnum and litter near vernal pool with Carex (1 ♂, 1 ♀, RWC).

Collection and habitat data.

Brunke et al. (2011) reported that Staphylinus ornaticauda was restricted to wetlands, such as bogs and fens, with an abundance of sphagnum moss. In New Brunswick, this species appears to be associated with eastern white cedar swamps and fens and red maple swamps on calcareous soils. Adults were collected in eastern white cedar swamps, an eastern white cedar, red maple, and black ash (Fraxinus nigra Marsh.) swamp, and in a red maple swamp near an eastern white cedar swamp. Adults occurred in litter at the base of cedars, and in moist litter and moss near small vernal pools with Carex. Adults were collected by sifting litter. This species was collected in April, May, and June. This species is flightless (Brunke et al. 2011). Due to the limited dispersal capabilities, restricted habitat requirements, and apparent rarity, Brunke et al. (2011) suggested that this species should be studied as a potential species at risk.

Distribution in Canada and Alaska.

MB, ON, PQ, NB, NS (Campbell and Davies 1991, as Staphylinus erythropterus Linnaeus).

Map 27.

Collection localities in New Brunswick, Canada of Staphylinus ornaticuada.

Subtribe Philonthina Kirby, 1837
Bisnius cephalicus Casey, 1915**

http://species-id.net/wiki/Bisnius_cephalicus

Map 28
Material examined.

New Brunswick, Restigouche Co., 7.5 km S of Saint Arthur, 47.8283°N, 66.7654°W, 14.VI.2006, R. P. Webster, old-growth eastern white cedar forest in moist leaves at base of large white birch (1 ♂, 1 ♀, NBM, RWC); Berry Brook P.N.A., 47.8140°N, 66.7578°W, 26.V.2007, R. P. Webster, old-growth eastern white cedar swamp, in moss and leaf litter under alders (1 ♂, 1 ♀, RWC); MacFarlane Brook P.N.A., 47.6018°N, 67.6263°W, 25.V.2007, R. P. Webster, old-growth eastern white cedar swamp, in moss and leaves under alders near brook (1 ♀, RWC); Jacquet River Gorge P.N.A., 47.8204°N, 66.0833°W, 14.VI.2008, R. P. Webster, river margin in drift material (1 ♂, RWC).

Collection and habitat data.

Little was previously known about the habitat requirements of this species. In New Brunswick, this species was found in leaf litter and moss near brooks in old-growth eastern white cedar forests and in drift material along a river margin (1). Adults were collected in May and June.

Distribution in Canada and Alaska.

AB, MB, ON, NB (Smetana 1995). This species was previously known from only three specimens from two localities, a single female from the type locality at “Aweme”, Manitoba and two specimens from George Lake, Alberta (Smetana 1995) Recently, Brunke and Marshall (2011) reported another specimen of this species from N. Moosonee, Ontario.

Map 28.

Collection localities in New Brunswick, Canada of Bisnius cephalicus.

Bisnius cephalotes (Gravenhorst, 1802)

http://species-id.net/wiki/Bisnius_cephalotes

Remarks.

Bisnius cephaloteswas reported by Majka and Klimaszewski (2008a) from New Brunswick based on three specimens collected by R. P. Webster from New Maryland. There are no specimens of this species in the collections of R. P. Webster or C. Majka from New Brunswick. This species is, therefore, removed from the faunal list of New Brunswick.

Bisnius palmi Smetana, 1955

http://species-id.net/wiki/Bisnius_palmi

Map 29
Material examined.

New Brunswick, Queens Co., near Quarries, 45.6005°N, 66.0500°W, 25.IX.2006, S. Makepeace, contents from barred owl nest box, 8 m high on red maple (1, ♀, RWC); 4 km W of Lower Gagetown, 45.7466°N, 66.1862°W, 30.VII.2006, S. Makepeace, mixed red oak and pine forest, contents of red shouldered hawk nest 12 m high in red oak (3 ♂, 2 ♀, RWC); Pleasant Villa, 45.7023°N, 66.1732°W, 15.VI.2007, S. Makepeace & R. Webster (1, ♀, NBM); Rees, near Grand Lake, 46.0016°N, 65.9466°W, 29.V.2007, S. Makepeace & R. Webster, nest box contents of barred owl (4 ♂, 6 ♀ NBM, RWC); McAlpines near Upper Hampstead Rd., 45.7250°N, 66.1200°W, 3.VI.2007, S. Makepeace & R. Webster, nest contents of barred owl (1 ♂, 1 ♀, NBM); Cranberry Lake P.N.A., 46.1125°N, 65.6075°W, 7–22.VI.2011, 13–20.VII.2011, M. Roy & V. Webster, old red oak forest, Lindgren funnel traps in forest canopy (2 ♂, NBM). Sunbury Co., Noonan, 45.9923°N, 66.4099°W, 2.VI.2007, S. Makepeace & R. P. Webster, nest contents of barred owl from tree hole 7 m high in red maple (1 ♀, NBM). Westmorland Co., Sackville, near Ogden Mill, 45.9216°N, 64.3893°W, 12.V.2006, S. Makepeace, black spruce forest, in nest contents of great horned owl, Bubo virginianus (2 ♀, NBM, RWC). York Co., Graham Corner, 45.8565°N, 67.7083°W, 26.VI.2007, S. Makepeace & R. Webster, nest contents of barred owl from tree hole in sugar maple (1 ♂, 1 ♀, NBM); Marysville, 45.9750°N, 66.5700°W, 22.VI.2007, S. Makepeace & R. Webster, nest box contents of barred owl (1 ♀, NBM).

Collection and habitat data.

This species was reported by Smetana (1995) from various habitats associated with trees, such as swallow nests, old squirrel nests, and a red oak tree fork hole. In New Brunswick, all but one of the Bisnius palmi specimens were found in the nest contents of a great horned owl (Bubo virginianus Gmelin) and barred owls, which normally nest in tree holes or in artificial nest boxes on trees. This species was also found in the nest contents of a red shouldered hawk (Buteo lineatus Gmelin), which makes large nests within forks of large trees. One adult was captured in a Lindgren funnel trap deployed in the canopy of a red oak in an old red oak forest. Adults were collected in May, June, July, and September.

Distribution in Canada and Alaska.

ON, NB, NS (Smetana 1995). Bisnius palmi is transcontinental in North America, with most records from eastern North America. There is one record from Nova Scotia (Caribou Island). Bisnius palmi was originally described from Sicily, Italy, but was apparently an accidental, introduced specimen (Smetana 1995).

Map 29.

Collection localities in New Brunswick, Canada of Bisnius palmi.

Bisnius quediinus Horn, 1884**

http://species-id.net/wiki/Bisnius_quediinus

Map 30
Material examined.

New Brunswick, Queens Co., Cranberry Lake P.N.A., 46.1125°N, 65.6075°W, 21–27.V.2009, R. Webster & M.-A. Giguère, mature red oak forest, Lindgren funnel traps (2 ♀, 1 sex undetermined, AFC, RWC); Grand Lake Meadows P.N.A., 45.8227°N, 66.1209°W, 13–25.V.2011, 2–21.VI.2011, 5–19.VII.2011, M. Roy & V. Webster, old silver maple forest and seasonally flooded marsh, Lindgren funnel traps (3, AFC, NBM, RWC). Restigouche Co., Dionne Brook P.N.A., 47.9030°N, 68.3503°W, 27.VI-14.VII.2011, M. Roy & V. Webster, old-growth northern hardwood forest, Lindgren funnel trap (1, NBM). Sunbury Co., Acadia Research Forest, 45.9866°N, 66.3841°W, 28.IV-4.V.2009, 25.V-2.VI.2009, R. Webster & M.-A. Giguère, mature (100 year-old) red spruce forest with scattered red maple and balsam fir, Lindgren funnel traps (1 ♂, 1 sex undetermined, AFC, RWC). York Co. New Maryland, off Hwy 2, E of Baker Brook, 45.8760°N, 66.6252°W, 6.IV.2005, R. P. Webster, old growth eastern white cedar swamp, in moss and litter at base of cedar (1 ♂, 1 ♀, RWC); 15 km W of Tracy, off Rt. 645, 45.6848°N, 66.8821°W, 4–11.V.2009, 11–19.V.2009, 28.VI-7.VII.2009, R. Webster & M.-A. Giguère, mature (120- 180 year-old) red pine forest, Lindgren funnel traps (1 ♀, 2 sex undetermined, AFC, RWC); Charters Settlement, 45.8395°N, 66.7391°W, 16–23.V.2009, R. P. Webster, mixed forest, Lindgren funnel trap (1 ♂, RWC).

Collection and habitat data.

Little is known about the habitat associations of this species. Smetana (1995) speculated that it might live in burrows of mammals or, less likely, in bird nests. Two specimens from New Brunswick were found in moss at the base of a tree in an old-growth eastern white cedar swamp early in the season when some snow and ice were still present. This was possibly an overwintering site. Most specimens were captured in Lindgren funnel traps deployed in a variety of forest types (red pine, red oak, red spruce, mixed forest, old-growth northern hardwood forest). These traps mimic tree trunks (Lindgren 1983), and it is possible that this species lives in microhabitats associated with standing trees. Adults were collected in April, May, June, and July.

Distribution in Canada and Alaska.

QC, NB (Smetana 1995). This rare species was known from only a few localities in Quebec south to Massachusetts and west to Michigan, Kansas, and South Dakota (Smetana 1995).

Map 30.

Collection localities in New Brunswick, Canada of Bisnius quediinus.

Erichsonius alumnus Frank, 1975**

http://species-id.net/wiki/Erichsonius_alumnus

Map 31
Material examined.

New Brunswick, Charlotte Co., ca. 9 km NW of New River, 45.2067°N, 66.6505°W, 13.VI.2008, R. P. Webster, alder swamp near large brook, treading vegetation along brook margin (1 ♀, NBM). Restigouche Co., Little Tobique River near Red Brook, 47.4465°N, 67.0689°W, 13.VI.2006, R. P. Webster, river margin, under debris on clay and sand mix (3 ♂, 5 sex undetermined, RWC). York Co., Charters Settlement, 45.8404°N, 66.7360°W, 27.V.2008, R. P. Webster, brook margin partially shaded by alders, among cobblestones and gravel (1 ♂, RWC); near Mazerolle Settlement, N of Hwy 2 near exit 271, 45.8764°N, 66.8260°W, 7.VI.2008, R. P. Webster, brook margin in beaver meadow, in fine gravel/clay mixed with grass (1 ♂, RWC); 8.4 km W of Tracy, off Rt. 645, 45.6821°N, 66.7894°W, 14.V.2008, R. P. Webster, alder swamp near brook, in leaf litter and grass on hummock (1, NBM).

Collection and habitat data.

Erichsonius alumnus appears to be a riparian species associated with river and brook margins. Records in Frank (1975) included individuals from banks of streams, on mud by a brook, and an individual collected by treading mud by a stream. In New Brunswick, the largest series was collected along a river margin under debris on a sand–clay mix. Other adults were collected from brook margins in alder swamps and a beaver meadow. Adults occurred in grass litter mixed with fine gravel and clay, among cobblestones and gravel, and leaf and grass litter from these brook margin habitats. This species was collected in May and June.

Distribution in Canada and Alaska.

ON, QC, NB (Frank 1975).

Map 31.

Collection localities in New Brunswick, Canada of Erichsonius alumnus.

Erichsonius inutilis (Horn, 1884)**

http://species-id.net/wiki/Erichsonius_inutilis

Map 32
Material examined.

New Brunswick, Queens Co., W of Jemseg at “Trout Creek”, 45.8231°N, 66.1245°W, 11.IV.2006, R. P. Webster, silver maple swamp, sifting leaf litter from crotch of silver maple with multiple trunks (1 ♂, 1 sex undetermined, RWC); near Queenstown, 45.6904°N, 66.1455°W, 13.V.2008, R. P. Webster, old hardwood forest, in leaf litter in seepage area near small brook (2 ♂, 1 sex undetermined, RWC); ca. 3.5 km W of Lower Gagetown, 45.7497°N, 66.1846°W, 13.V.2008, R. P. Webster, mature red oak and red maple forest, in moist leaves on margin of vernal pond (1, RWC). York Co., Mazerolle Settlement, 45.8729°N, 66.8311°W, 28.IV.2006, R. P. Webster, stream margin (sun-exposed), in grass litter on muddy soil (1 ♂, RWC); Kelly’s Creek at Sears Road, 45.8723°N, 66.8414°W, 7.VI.2008, R. P. Webster, Carex marsh, treading (1 ♂, RWC); Fredericton at Saint John River, 45.9598°N, 66.6258°W, 19.VII.2005, R. P. Webster, river margin, under drift material (1, RWC).

Collection and habitat data.

Little was previously known about the habitat associations of this species. The only records with habitat data reported in Frank (1975) included specimens sifted from flood debris, swamp grass, ex nest of a meadow vole (Microtus pennsylvanicus Ord), and one individual collected in a tamarack bog. In New Brunswick, this species appears to be associated with moist to wet habitats in forested areas, including seepage areas near small brooks, vernal pond margins, stream and river margins, and Carex marsh. Adults were sifted from moist leaves, grass litter on muddy soil, drift material, and by treading Carex. A few adults were sifted from leaf litter from the crotch of a silver maple with multiple trunks in early April in a silver maple swamp. This was presumably an overwintering site for these adults. Adults were collected during April, May, June, and July.

Distribution in Canada and Alaska.

ON, QC, NB (Frank 1975).

Map 32.

Collection localities in New Brunswick, Canada of Erichsonius inutilis.

Erichsonius parcus (Horn, 1884)**

http://species-id.net/wiki/Erichsonius_parcus

Map 33
Material examined.

New Brunswick, York Co., New Maryland, U.N.B. Woodlot, 45.9116°N, 66.6698°W, 26.V.2008, R. Webster, G. Forbes, & M.-A. Giguère, abandoned beaver lodge occupied by muskrats, in wall of lodge (4 ♂, 2 ♀, RWC).

Collection and habitat data.

Little was previously known about the habitat associations of Erichsonius parcus. The specimens from New Brunswick were collected from the wall of an abandoned beaver lodge occupied by muskrats. In Rhode Island (USA) (Washington Co., 2 mi S of Shannock, 41.4270°N, 71.6039°W, 22.IV.2007), three specimens were sifted from moist leaves on the margin of a vernal pond (Webster, unpublished data) in a red maple swamp.

Distribution in Canada and Alaska.

ON, NB (Brunke and Marshall 2011). Erichsonius parcus was reported from Massachusetts, south to Virginia, South Carolina, and Louisiana in the USA by Frank (1975).

Map 33.

Collection localities in New Brunswick, Canada of Erichsonius parcus.

Erichsonius patella (Horn, 1884)

http://species-id.net/wiki/Erichsonius_patella

Map 34
Material examined.

New Brunswick, Queens Co., Grand Lake near Scotchtown, 45.8762°N, 66.1816°W, 25.V.2006, R. P. Webster, lakeshore, in drift material (1 ♂, RWC); Rees, near Grand Lake, 46.0016°N, 65.9466°W, 29.V.2007, S. Makepeace & R. Webster, coll., nest box contents of barred owl (1 ♀, NBMB). Sunbury Co., Acadia Research Forest, 45.9866°N, 66.3841°W, 19–25.V.2009, R. Webster & M.-A. Giguère, mature (110 year-old) red spruce forest with scattered red maple and balsam fir, Lindgren funnel trap (1 ♀, AFC). York Co., Charters Settlement, 45.8340°N, 66.7450°W, 15.V.2004, 30.V.2004, 10.VI.2004, 27.IV.2005, R. P. Webster, mixed forest, under conifer bark in wood pile (4 sex undetermined, RWC); same locality and collector but 45.8300°N, 66.7360°W, 20.VI.2004, R. P. Webster, mature mixed forest, in leaf litter near stream (1, RWC); same locality and collector but 45.8395°N, 66.7391°W, 28.IX.2005, mixed forest, in compost (decaying vegetables) (1 ♂, RWC); Fredericton, Odell Park, 45.9570°N, 66.6695°W, 19.VI.2005, R. P. Webster, in pile of woodchips and decaying plant materials (1 ♂, 1 sex undetermined, RWC); Nashwaaksis River at Rt. 105, 45.9850°N, 66.6900°W, 6.V.2006, R. P. Webster, upper river margin in flood debris (1, RWC); Kelly’s Creek at Sears Road, 45.8723°N, 66.8414°W, 7.VI.2008, R. P. Webster, alder swamp with red maple, in moist leaf and grass litter near vernal pool (1 sex undetermined, NBM); 15 km W of Tracy, off Rt. 645, 45.6848°N, 66.8821°W, 18.V-2.VI.2010, R. Webster & C. MacKay, mature (120–180 year-old) red pine forest, Lindgren funnel trap (1, AFC).

Collection and habitat data.

This species appears to be associated with various kinds of decaying organic materials. The few records with habitat data reported in Frank (1975) included adults collected from human dung, sifting leaves, sifting oak leaves, in ground cover in a white pine forest, ex mushrooms, funnel extract of mixed litter, Rhododendron litter, and pine–hardwood leaf litter near a stream edge. In New Brunswick, adults were found in a variety of decaying organic material, including drift material along a lakeshore, flood debris on an upper river margin, leaf litter near a stream, moist leaf and grass litter near a vernal pool, under conifer bark in a wood pile, in compost (decaying vegetables), in a pile of woodchips, and on decaying plant material. A few individuals were captured in Lindgren funnel traps. Most collections were from forested habitats. One adult was collected from the nest contents of a barred owl. Adults were collected in April, May, and June.

Distribution in Canada and Alaska.

ON, QC, NB, NS (Frank 1975; Bishop et al. 2009).

Map 34.

Collection localities in New Brunswick, Canada of Erichsonius patella.

Erichsonius