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1 March 2012 Psocopteran Species Associated with Eastern Hemlock in the Southern Appalachians
Carla Coots, Paris Lambdin, Jerome Grant, Rusty Rhea, Edward Mockford
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Eastern hemlock, Tsuga canadensis (L.) Carrière, comprises a vital component of biological diversity (Jordan & Sharp 1967; Lapin 1994; Tingley et al. 2002; Buck 2004; Buck et al. 2005; Dilling et al. 2007; Dilling et al. 2009) and economical (Travel Industry Association 2006; Woodsen 2001) and environmental stability (Evans 2002; Snyder et al. 2004) within its geographical range. Hemlock woolly adelgid, Adelges tsugae Annand (Hemiptera: Adelgidae), is an exotic insect species capable of rapidly reducing populations of eastern hemlock throughout the eastern United States (McClure & Fergione 1977; Buck et al. 2005; Ellison et al. 2005). As such, documenting the biodiversity of insects associated with this host tree is imperative. More than 400 insect species have been recorded to be associated with eastern hemlock in the southern Appalachians (Wallace & Hain 2000; Buck et al. 2005; Lynch et al. 2006; Dilling et al. 2007; Dilling et al. 2009).

Psocopterans comprise a major component of arthropod diversity on eastern hemlock, occupying an important ecological role as major consumers of microepiphytes as well as an integral food source for predators (Thornton 1985; Mockford 1993). Population densities of psocopterans can be extremely high. For example, densities of Psocoptera on the bark of larch, i.e., Larix decidua Mill., have been reported at > 4,000/m2, which Thornton (1985) equates to > 6,000/m2 of land surface. In this study, we document the psocopteran richness within the canopy of eastern hemlock in the southern Appalachians.

Eastern hemlocks (n = 6) were selected on 5 Nov 2005 at Indian Boundary within the Cherokee National Forest located in Monroe County in southeast Tennessee (35°23.787 N, 84°06.662 W). All trees (14–18 m in height) were located in a shortleaf pine—oak (type 76) forest (Eyre 1980). Because of the diversity of habitat preferences in trees and mobility among species of Psocoptera, 3 sampling methods were selected to capture a wide range of psocopteran species and were executed monthly from Nov 2005 through Sep 2008. Also, a platform lift was used to sample the bottom, middle and top stratum on each tree in Aug 2006, Sep 2007, and Jun 2008. Specimens were collected using direct sampling (beat sheet, handpicking, and trunk vacuuming) with collected specimens placed into labeled (date, site and tree location, sampling type) alcohol-filled vials and taken to the laboratory for identification. Beat-sheet samples (4 per tree) were taken at each direction by striking each branch 5 times with a one-meter rod, while visual observations were conducted on each tree for 5 min per stratum, and direct trunk vacuuming occurred on 61 cm of the circumference of the tree's trunk.

During this study, 3,740 adult and nymph psocopteran specimens were collected and identified, representing 44 species, 23 genera, and 11 families (Table 1). These species represent 14.3% of the species (307) and 41% of the families of Psocoptera documented in North America (Mockford 1993; Lienhard & Smithers 2002). In addition, 29 species represent new records for Tennessee and 33 species represent new county records for the state. The number of psocopteran species on eastern hemlock comprises almost 10% of the known insect species associated with this host tree.

The greatest number of species was recorded for Psocidae followed by Lachesillidae and Peripsocidae. Species within these 3 families represent 37%, 23%, and 11%, respectively, of the total species identified on eastern hemlock. The families Dasydemellidae, Lepidopsocidae, Mesopsocidae, Myopsocidae, and Stenopsocidae were each represented by only 1 species. However, the least number of specimens for a species was collected for Lachesilla andra Sommerman (n = 16) (Lachesillidae) followed by L. anna Sommerman (n = 22), Peripsocus stagnivagus Chapman (n = 27) (Peripsocidae), and Lachesilla corona Chapman (n = 29) (Lachesillidae). The greatest number of specimens was collected for Cerastipsocus venosus (Burmeister) (n = 246) (Psocidae) followed by Valenzuela flavidus (Stevens) (n = 201) (Caeciliusidae). Species identified from eastern hemlock constitute the highest number of psocopteran species recorded from a single tree species.

The dominant distribution pattern of the species identified is the eastern deciduous forest pattern as defined and described by Mockford (1993) (i.e., corresponding with delimited eastern deciduous forest (Braun 1972) in the eastern United States). This eastern deciduous forest pattern is noted as having poorly documented northern delineation due to limited collecting in this area, but generally is found from central New Brunswick to central Ontario and southward to peninsular Florida. Lachesilla pedicularia (L.) and Teliapsocus conterminus (Walsh) were noted as having other distribution patterns (Mockford 1993). In the eastern United States, T. conterminus (Walsh) generally follows the eastern deciduous forest pattern but has a southern limit that extends farther into Florida (Mockford 1993). Lachesilla pedicularia is noted as having a large outdoor range, and as such does not fit into a specific distribution pattern. Distribution of male Ptycta polluta (Walsh) was documented to be the southern Appalachians in Tennessee (Mockford 1993) with bisexual populations of P. polluta and Peripsocus subfasciatus (Rambur) appearing to be restricted to hemlock stands. Graphopsocus cruciatus (L.) has been classified as an introduced species (Mockford 1993), and has a varied distribution, including Tennessee, in the eastern and western United States, where it has been documented most often from areas around coastal waterways and inlets. The majority of the species identified are noted as having a variety of habitat preferences and broad distribution range (Table 1).







Psocopterans collected (3,740) represented 44 species, 23 genera, and 11 families. Most species of Psocoptera found in association with eastern hemlock in the southern Appalachians exist on a variety of vegetative hosts, and as such their population numbers should be minimally impacted by any decline in eastern hemlock populations. However, loss of eastern hemlock populations could be detrimental to a few species (i.e., P. polluta and P. subfasciatus) that are dependent upon this host for survival. Of those species identified, 29 represent new records for Tennessee and 33 species represent new county records for the state.



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Carla Coots, Paris Lambdin, Jerome Grant, Rusty Rhea, and Edward Mockford "Psocopteran Species Associated with Eastern Hemlock in the Southern Appalachians," Florida Entomologist 95(1), 224-227, (1 March 2012).
Published: 1 March 2012
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