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1 December 2015 Seasonal Abundance of Thysanoptera Species in Tillandsia usneoides (Poales: Bromeliaceae)
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Abstract

Spanish moss, Tillandsia usneoides (L.) (Poales: Bromeliaceae), is widely distributed in the southeastern United States. A diversity of arthropod species from numerous taxa are known to inhabit this common epiphytic plant. Thysanoptera species inhabiting Spanish moss were sampled monthly over the course of a year from trees in 4 different genera and included 10 species of thrips from 8 genera and 3 families represented. Breeding populations of predatory Karnyothrips (Phlaeothripidae) were common in Spanish moss during all months of the year. The adults of 2 phytophagous species of Frankliniella (Thripidae) were common in the spring months, but only a few larvae were collected over the course of the year. The adults of other species collected were: Heterothrips quercicola J. C. Crawford (Heterothripidae); Chilothrips pini Hood, Neohydatothrips variabilis (Beach), and Selenothrips rubrocinctus (Giard) (Thripidae); and Hoplandrothrips pergandei Hinds and Liothrips ocellatus Hood (Phlaeothripidae). Although a diverse group of phytophagous thrips species inhabited Spanish moss, there was little evidence that it was a host. It may simply have been a temporary shelter with no other biological significance. The predatory thrips were abundant probably feeding on the diverse group of small arthropods that inhabit Spanish moss.

Spanish moss, Tillandsia usneoides (L.) (Poales: Bromeliaceae), is an epiphytic plant that ranges from the coastal plain of the southeastern USA extending through Central America south to Argentina and Chile (Garth 1964). Spanish moss obtains its minerals and moisture from atmospheric conditions as it has no absorbing root system but instead possesses absorbing scales over the entire plant. It is best adapted to welllighted, moist habitats and requires high relative humidity and regular rains in order to sustain optimal growth. It has a scorpioid dichotomous growth pattern. Growth of the plant is proportional to visible solar radiation, and more plants will be found on the most exposed areas of the tree (Garth 1964). Spanish moss flowers between mid-Apr and early Jun in Georgia, USA, but every plant does not flower every year.

Young & Lockley (1989) studied the diversity and seasonal abundance of species of arthropods inhabiting Spanish moss. No thrips were reported from the 2,600 arthropods collected. Whitaker & Ruckdeschel (2010) were interested primarily in the seasonal abundance of mites in Spanish moss, although the total number of thrips of all species was reported. Thrips were most abundant in the spring. More thrips were found in the Spanish moss that had fallen to the ground than that remaining on the trees.

Funderburk et al. (2015) reported the population dynamics of Frankliniella bispinosa (Morgan) (Thysanoptera: Thripidae) on crepe myrtle, Lagerstroemia indica L. × fauriei Koehne (Myrtales: Lythraceae). Populations were almost completely aggregated in the flowers over the leaves. The adults and very rarely the larvae were found on the Spanish moss epiphytic on the trees. Two species of Karnyothrips (Thysanoptera: Phlaeothripidae), predators of small insects, were common in the Spanish moss, and other thrips species were collected. The purpose of this study was to determine the diversity and seasonal abundance of thrips inhabiting Spanish moss in North Florida, USA.

Materials and Methods

EXPERIMENTAL LOCATIONS

Spanish moss was collected monthly between Dec 2011 and Nov 2012 from oak (Quercus sp.) (Fagales: Fagaceae), pecan (Carya illinoiensis [Wangenheim] K. Koch; Fagales: Juglandaceae), and sweet gum (Liquidambar styraciflua L.; Saxifragales: Altingiaceae) in Gadsden County, Florida, USA (30°32′52″N, 84°35′36″W); and oak and dogwood (Cornus florida L.; Caryophyllales: Cornaceae) in Leon County, Florida, USA (30°28'37”N, 84°21′30″W).

SAMPLING SPANISH MOSS FOR THRIPS

Sampling procedures were modified from Funderburk et al. (2015). Five samples of 3.8 L bags of moss were collected from each tree species monthly. Samples were collected between 2:00 and 4:00 p.m. Eastern Standard Time or Eastern Daylight Time. Samples were carried immediately to the laboratory and placed in a freezer for at least 24 h, after which time the samples were removed from the freezer and allowed to come to room temperature. Rinsing methods were derived from those used by Frank et al. (2004) on bromeliads and modified by Funderburk et al. (2015) for Spanish moss. Each bag was filled with water, the Spanish moss was agitated in the water, and the water was drained through a sieve to catch the thrips. This was repeated 4 more times. The contents were placed into 70% ethyl alcohol, and the thrips were separated from other materials under a microscope with 40× magnification. Thrips were mounted on slides for identification.

VOUCHERS

Keys used in identification included Mound & Marullo (1996) and Vierbergen et al. (2010). Comparisons were made with the Thysanoptera collections at the Natural History Musuem, London, United Kingdom, and at the Systematic Entomology Laboratory, Beltsville, Maryland, USA. Voucher specimens are located at the collection at the North Florida Research and Education Center, University of Florida, in Quincy, Florida, USA.

Results

Ten thrips species belonging to 8 genera and 3 families were found in the Spanish moss samples (Table 1). The species were Heterothrips quercicola J. C. Crawford (Heterothripidae); Chilothrips pini Hood, F. bispinosa, Frankliniella tritici (Fitch), Neohydatothrips variabilis (Beach), Selenothrips rubrocinctus (Giard) (Thripidae); and Hoplandrothrips pergandei Hinds, Liothrips ocellatus Hood, Karnyothrips harti (Hood), and Karnyothrips melaleucus (Bagnall) (Phlaeothripidae). In total, 651 adult thrips were collected. Species of Frankliniella and Karnyothrips were 83 and 16%, respectively, of the total adult thrips collected. The adults of F. bispinosa, F. tritici, K. harti, and K. melaleucus were common species in the moss collected from all trees.

Table 1.

The number of male and female adults of each thrips species collected from five 3.8 L samples of Tillandsia usneoides epiphytic on trees of different species in Leon and Gadsden Counties, Florida.

t01_1179.gif

The total number of Frankliniella species larvae collected was less than 1% of the total number of Frankliniella adults collected (Table 2); therefore, the Spanish moss was not a host plant species used for breeding. The total number of Karnyothrips species larvae collected was about 55% of the total number of Karnyothrips adults collected (Table 2); therefore, the Spanish moss was utilized as habitat for breeding. The larvae of S. rubrocinctus were collected from Spanish moss on sweet gum during Nov, Jan, and Feb (Table 2).

Discussion

The same Frankliniella and Karnyothrips species commonly were collected from Spanish moss epiphytic on L. indica × fauriei in Leon County, Florida (Funderburk et al. 2015). The phytophagous F. bispinosa and F. tritici are the most common species of thrips in flowers in northern Florida (Paini et al. 2007). All Karnyothrips are predatory on small arthropods (Mound 2005).

The adults of F. bispinosa and F. tritici are highly dispersive in their behavior (Ramachandran et al. 2001) and, as a result, land on a wide range of substrates including plants that are not hosts. Frankliniella adults were collected in this study mostly during Apr and May, which coincides with the traditional period of greatest population abundance and movement on crop (Ramachandran et al. 2001) and uncultivated hosts (Paini et al. 2007). The adults may simply have used the Spanish moss as a landing place, or the Spanish moss may have served as an important feeding or behavioral resource.

Funderburk et al. (2015) previously reported that Spanish moss was habitat for reproduction of Karnyothrips. Small arthropods including Acari, Psocoptera, Collembolla, and Coccidae are common inhabitants of Spanish moss (Whitaker & Ruckdeschel 2010). This suggests an abundance of suitable prey for both adult and larval Karnyothrips. Insects in the order Thysanoptera are mainly phytophagous or mycophagous, and obligate predation is limited to only several lineages (Mound 2005).

Selenothrips rubrocinctus is common throughout the Neotropics feeding on the leaves and fruits of cacao, Theobroma cacao L. (Malvales: Malvaceae) (Fennah 1965). The species is collected rarely in northern Florida, although dense populations were recorded recently in Leon County in Florida from Rosa species (Rosales: Rosaceae) in Feb 2013 (J. F., unpublished). The restless behavior of thrips can obscure biological significance. Many host-plant records represent nothing more than thrips finding places with no other biological significance (Mound 2013). There was no indication that Spanish moss was a host or even an important shelter for L. occellatus, H. pergandei, N. variabilis, C. pini, and H. quercicola. At most, a few adults of each of these species were collected over the course of the study, and no larvae of these species were collected.

Table 2.

The number of adult and larval thrips of each species collected monthly between Dec 2011 and Nov 2012 from five 3.8 L samples Tillandsia usneoides in Leon and Gadsden Counties, Florida.

t02_1179.gif

In this study, the thrips fauna of Spanish moss epiphytic on Quercus species, C. illinoiensis, L. styraciflua, and C. florida were very similar to the results of the thrips fauna of Spanish moss epiphytic on L. indica L. × fauriei reported by Funderburk et al. (2015). Two species of Karnyothrips were common reproducing year-round. The adults of Frankliniella were common during the spring.

Acknowledgments

We thank Paul Brown (Senior Curator, The Natural History Museum, London, United Kingdom) and Laurence Mound (Australian National Insect Collection, Canberra, Australia) for assistance with Thysanoptera collections.

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Ozan Demirozer, Kara Tyler-Julian, and Joe Funderburk "Seasonal Abundance of Thysanoptera Species in Tillandsia usneoides (Poales: Bromeliaceae)," Florida Entomologist 98(4), 1179-1181, (1 December 2015). https://doi.org/10.1653/024.098.0424
Published: 1 December 2015
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