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1 March 2016 Host Range of Caloptilia triadicae (Lepidoptera: Gracillariidae): An Adventive Herbivore of Chinese Tallowtree (Malpighiales: Euphorbiaceae)
J. G. Duncan, M. S. Steininger, S. A. Wright, G. S. Wheeler
Author Affiliations +

An adventive herbivore of the invasive weed Chinese tallowtree (Triadica sebifera [L.] Small; Malpighiales: Euphorbiaceae) first appeared in North America in 2004. Identified as a Caloptilia triadicae Davis (Lepidoptera: Gracillariidae), this leaf miner was found damaging T. sebifera saplings. In Gainesville, Florida, we exposed naturalized populations of C. triadicae to Chinese tallowtree and related plant species in multiple-choice tests. Our findings indicated that the larvae of this species had a narrow host range as they readily fed and completed development on Chinese tallowtree leaves. The only exception to this specificity was larval feeding and development on the native oysterwood, Gymnanthes lucida Sw. (Malpighiales: Euphorbiaceae). Naturalized populations of C. triadicae were also found in Miami-Dade and Broward Counties, Florida, feeding and developing on ornamental populations of G. lucida.

Chinese tallowtree, Triadica sebifera (L.) Small (Malpighiales: Euphorbiaceae), native to China, is one of the most aggressive and widespread invasive weeds in temperate forests and marshlands of the southeastern USA (Bruce et al. 1997). Chinese tallowtree (hereafter “tallow”) was estimated to cover nearly 185,000 ha of southern forests ( 2015). Since its introduction, the weed has been reported primarily in 10 states including North Carolina, South Carolina, Georgia, Florida, Alabama, Mississippi, Louisiana, Arkansas, Texas, and California (EddMapS 2015). Tallow is now a prohibited noxious weed in Florida, Louisiana, Mississippi, and Texas (USDA/NRCS 2015). As the existing range of tallow is expected to increase, the projected timber loss, survey, and control costs will also increase. Cost estimates for controlling tallow infestations in forestlands of eastern Texas, Louisiana, and Mississippi range from $200 million to $400 million in the next 20 yr (Wang et al. 2012a). Tallow invades mesic flatwoods, scrubby flatwoods, alluvial floodplain forests, strand swamps, and ruderal communities. Chemical and mechanical control measures have been used with short-term success. However, long-term, cost-effective maintenance programs that integrate several control methods are required to prevent regrowth and recruitment (Jubinsky & Anderson 1996). Herbivory, through classical biological control, can provide an ecologically sound, cost-effective, and sustainable management solution to protect native plants in these habitats (Wheeler & Ding 2014).

One significant factor in the success of tallow in its invaded range is the historical lack of specialized herbivores that exert population-level regulation (Harcombe et al. 1993; Bruce et al. 1997). Herbivores in the USA that feed on tallow include mostly generalists, such as Melanoplus angustipennis (Dodge) and Orphullela pelidna Burmeister (Orthoptera: Acrididae) (Siemann & Rogers 2003; Lankau et al. 2004). The only herbivore with a narrow host range found feeding on tallow in its invaded range is the moth Caloptilia triadicae Davis (Lepidoptera: Gracillariidae). The early instars of this species mine the leaves, whereas the last instars cut out a leaf section and create a distinctive helical retreat where pupation occurs (Davis et al. 2013). This adventive species has now been reported from nearly all the tallow-infested areas of the southeastern USA (Fox et al. 2012). Caloptilia triadicae is thought to be of Chinese origin and was first discovered in the invaded range in 2004 (Fox et al. 2012).

Research on the biological control of tallow began in 2007 and identified a number of promising candidates from the weed's native range (Wheeler & Ding 2014). These candidates include the defoliating/rootfeeding flea beetle Bikasha collaris (Baly) (Coleoptera: Chrysomelidae) and the defoliating moth Gadirtha fusca Pogue (Lepidoptera: Nolidae), both being tested in quarantine to determine suitability for biological control (Huang et al. 2011; Wang et al. 2012b; Pogue 2014). The compatibility of these potential agents with one another and other herbivores like C. triadicae is being examined. The goal of this study was to determine if C. triadicae posed a threat to other native or ornamental plants of the southeastern USA.

Plants. Tallow plant material was field collected as seeds, seedlings, or small plants in Alachua County, Florida, and cultured as potted plants and maintained in a secure area at the Florida Department of Agriculture and Consumer Services, Division of Plant Industry. Additional plants were grown from seeds and seedlings provided by E. Siemann (Rice University, Houston, Texas). Non-target species were purchased or field collected (Table 1). Tallow plants and non-target species were maintained year-round inside a hoop house, 15 × 25 m, covered with woven shade cloth (30% black). The cloth only provided shade and allowed passage of C. triadicae moths into the hoop house. To protect plant species sensitive to cold temperatures between mid-Nov and mid-Apr, the hoop house was covered with 2 layers of clear 40 × 50 feet (12.19 × 15.24 m) 6 mL Super Dura-Film (At Films, Inc., Edmonton, Canada). Temperature was set at 29 °C and maintained by a thermostatically controlled gas heater (Modine Effiency II), a vent at the back (Micro-grow Greenhouse Systems), and a fan at the front of the hoop house. Tallow and non-target plants were intermingled and haphazardly arranged inside the hoop house.

Production and maintenance of plants was similar to that described in Steininger et al. (2013). Test plants were routinely sprayed with soap and water and fungicides as needed to exclude pests and pathogens. Fungicides included Cleary Chemical 3336WP Turf and Ornamental Systemic Fungicide (1.0 mL/L of water) and Spectracide Immunox Multi-Purpose Fungicide Spray Concentrate (7.8 mL/L of water). The plants were fertilized (Scotts Peters General Purpose Florida 20-20-20) approximately every 2 to 4 mo according to label rate. Additionally, 1 top coat of Osmocote Plus 15-9-12 controlled-release granular fertilizer was added to each potted plant (3.7 g/L). Plants were hand watered 1 to 3 times a week as needed and were maintained either outdoors or in the hoop house.

Insects. Populations of C. triadicae appear to be multivoltine during much of the year in Florida. Mines have been observed most often on new growth. Adults and larvae appear early in the spring (May) and disappear, possibly entering diapause, during the winter (Nov) as tallow loses its leaves.

Table 1.

List of tallow (in bold) and non-target plant species exposed to natural populations of the leaf miner Caloptilia triadicae in open-field multiple-choice tests. Plant phylogeny follows Wurdack et al. (2005), Wurdack & Davis (2009), and Govaerts et al. (2015).


Host Range Tests. The target weed, T. sebifera is assigned to the Euphorbiaceae, in the order Malpighiales (Stevens 2015). We compiled a test plant list that included 41 species from the Euphorbiaceae family and relatives (Wurdack et al. 2005; Wurdack & Davis 2009; Govaerts et al. 2015). Members of the related families Phyllanthaceae and Putranjivaceae were also included (Stevens 2015). Host range tests were conducted with these closest relatives as they are considered most vulnerable to non-target damage and may be attacked by herbivores with narrow host ranges (Futuyma & Agrawal 2009). The list included native (e.g., Ditrysinia fruticosa [Bartram] Govaerts & Frodin, Gymnanthes lucida Sw.), ornamental (e.g., Euphorbia pulcherrima Willd. ex Klotzsch, Acalypha wilkesiana Müll. Arg.), and several threatened and endangered species (e.g., Hippomane mancinella L., Heterosavia bahamensis [Britton] Petra Hoffm.). Replicates generally included 7 to 8 (range 2 to 47) plants for tallow and non-target species (Table 1). Plant sources followed those previously described (Steininger et al. 2013).

Multiple-choice tests were conducted inside the hoop house during 2010 and 2011 in Gainesville, Florida, where plants of the target weed were also present as a control. Plants were observed daily, and when larval leaf mines or rolls were found, the plant was caged to see if adult C. triadicae would emerge. Alternatively, leaf mines were reared in cups (30 mL) and observed for adult emergence. Additional field observations of ornamental G. lucida plants were conducted in 2012 at Alice Wainwright and Crandon parks, Miami-Dade County, Florida, and at the United States Department of Agriculture, Agricultural Research Service (USDA/ARS), Invasive Research Lab in Broward County, Florida. Mature larvae were collected from flush growth and reared in the laboratory to determine if they could complete development on G. lucida. Adults that emerged were sent to a specialist (D. Davis, Smithsonian Institution, Washington, District of Columbia) who confirmed their identity.

During both 2010 and 2011, the C. triadicae infestation reached high densities in Gainesville, Florida, as 100% of the leaves were mined on T. sebifera saplings. Damage was so great that stem dieback was observed, and occasionally seedlings died from the impact of the larval feeding. The C. triadicae larvae fed and developed to adults on tallow and the non-target species G. lucida (Table 1). A few mines were found on H. mancinella and D. fruticosa but these larvae did not complete development. When leaf mines and rolls were found in 2010 on the non-target G. lucida, the plants were caged to see if adults would emerge, but none did. In 2011, all G. lucida plants (n = 8) were found damaged by C. triadicae larvae. One exuvia from an emerged C. triadicae adult was found in a G. lucida leaf roll suggesting that at least 1 individual completed development on G. lucida. In all, 14 C. triadicae pupae were found on G. lucida leaves and when caged, 2 adults, or 14% of the pupae, emerged. The suitability of G. lucida as a host of C. triadicae was confirmed as the native plant populations observed at Alice Wainwright Park in Miami-Dade County and the ornamental plantings at the USDA/ARS facility in Broward County were found infested with the moth.

Few herbivore species feed and develop on the invasive populations of tallow in its invaded range. Those that do feed on tallow are generalists that feed opportunistically while also damaging economically important species. Tallow plants grown in garden plots in Florida are routinely damaged by generalist larvae of Spodoptera latifascia Walker (Lepidoptera: Noctuidae) and adults of the invasive weevils Myllocerus undatus Marshall, Pachnaeus litus (Germar), and Diaprepes abbreviatus (L.) (Coleoptera: Curculionidae) (G. S. Wheeler, unpublished data). Tallow plants are visited by predators including Crematogaster species (Hymenoptera: Formicidae), possibly feeding on extrafloral nectar. The species C. triadicae is the first adventive moth with a narrow host range reported feeding on tallow in North America (Fox et al. 2012; Davis et al. 2013).

The distribution of the test plants that showed some degree of non-target damage has mostly little geographic overlap with that of tallow, with the exception of D. fruticosa. The native plants G. lucida and H. mancinella are only reported from the most southern counties of Florida (Miami-Dade and Monroe Counties) (Wunderlin & Hansen 2008). The species D. fruticosa occurs from north central Florida to east Texas (Wunderlin & Hansen 2008). In its invaded range, tallow is a temperate species, extending from North Carolina, along the Gulf States to east Texas (EddMapS 2015). In Florida, tallow occurs primarily north of Tampa, Orlando, and Daytona Beach (EddMapS 2015). However, ornamental plantings of G. lucida were found infested with the moth C. triadicae in sub-tropical Broward and Miami-Dade Counties. These infestations are over 400 km south of the major range of C. triadicoe-infested tallow (Leesburg, Florida). Although C. triadicae appeared to primarily feed on T. sebifera, its ability to use G. lucida as a host is of concern. Although damage appeared to be minor on G. lucida, the geographic range of C. triadicae could expand to include the Caribbean. Caribbean countries do not have invasive populations of T. sebifera, but endemic members of the genus Sapium, another close relative of T. sebifera, occur in Puerto Rico (USDA/NRCS 2015). These species were not included in our host range tests, but if C. triadicae disperses to the Caribbean, these species could be exposed to this seemingly beneficial introduced species. Considering the host range of C. triadicae, it is doubtful a release permit would have been pursued as a classical biological control agent of tallow.

We wish to acknowledge J. Lollis (USDA/ARS), who first observed a Caloptilia leaf-roll in the USDA laboratory and together with J. Gibson-Weston and R. Weaver provided technical assistance. Caloptilia triadicae specimens were generously identified by D. Davis, Smithsonian Institution, Washington, District of Columbia. DNA barcoding analysis was conducted by R. Hazen, Tulane University, Louisiana (GenBank accessions KF061045-KF061062). This research was partially funded by the Florida Fish and Wildlife Commission, the Florida Department of Environmental Protection (to G. S. Wheeler), and the USDA/ARS.

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J. G. Duncan, M. S. Steininger, S. A. Wright, and G. S. Wheeler "Host Range of Caloptilia triadicae (Lepidoptera: Gracillariidae): An Adventive Herbivore of Chinese Tallowtree (Malpighiales: Euphorbiaceae)," Florida Entomologist 99(1), 142-145, (1 March 2016).
Published: 1 March 2016
biological control of weeds
control biológico de malezas
multiple-choice test
pruebas de selección múltiple
Triadica sebifera
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