Current status of the biological control agent Neomusotima conspurcatalis (Lepidoptera: Crambidae), on Lygodium microphyllum (Polypodiales: Lygodiaceae) in Florida.
An indeterminate rachis and extensive rhizomatous growth smother native understory vegetation and act as a fire ladder carrying low-intensity fires into the canopy, which causes extensive tree death (Pemberton & Ferriter 1998). Compounding the challenge to control L. microphyllum is the strong propagule pressure from spores that travel via wind currents and arrive at isolated sites. No native herbivores exert control over the fern's growth and herbicides are difficult to apply in habitats in which L. microphyllum invades. Although herbicides and fire kill above-ground biomass, new fiddleheads rapidly regrow from the underground rhizome (Stocker et al. 2008).
In 1997, scientists from the U.S. and Australia conducted foreign exploration for biological control agents of L. microphyllum in Asia and Australia. These surveys yielded several insects and one mite that negatively impact L. microphyllum in the native range (Pemberton 1998; Goolsby et al. 2003). Of these candidates, 2 moths (Austromusotima camptozonale Yen and Neomusotima conspurcatalis Warren, Lepidoptera: Crambidae) and one leaf-galling mite (Floracarus perrepae Knihinicki & Boczek, Acariformes: Eriophyidae) were approved for release by the USDA-APHIS Technical Advisory Group (APHIS-TAG). Austromusotima camptozonale was released from 2004 until 2007 and then again from 2010 to 2012, but failed to establish despite the release of more than 160,000 adults and larvae into the field (Boughton & Pemberton 2008). Floracarus perrepae was released from 2008 until 2010 and has established within isolated patches in Martin County and Everglades National Park (Lake et al. in press).
Neomusotima conspurcatalis Warren (Lepidoptera: Crambidae) is a Lygodium specialist native to Southeast Asia and Australia. This agent readily established populations in Old World climbing fern stands after its introduction in early 2008. By Dec 2008, large larval populations were present in Jonathan Dickinson State Park and caused measurable impacts on L. microphyllum (Boughton & Pemberton 2009; Boughton unpublished data). However, two consecutive cold winters followed in 2010 and 2011 and moth populations decreased or were reportedly extirpated from previously established sites (Boughton et al. 2012a; Boughton & Pemberton 2012).
In late 2012, land managers once again began to report large larval feeding events, known as brown outs, in areas of Loxahatchee National Wildlife Refuge, Jonathan Dickinson State Park, and Barley Barber Swamp Conservation Area (pers. com). To verify these reports and determine the current status of N. conspurcatalis populations, we resurveyed all original release sites (N = 18) from Oct 2012 to Mar 2013. Each site was searched by 2 investigators for approximately 30 min and then assigned an infestation score (0-5), according to the frequency of occurrence of characteristic leaf feeding damage and abundance of N. conspurcatalis. Sites where N. conspurcatalis was absent were assigned a score of 0; old signs of feeding, but no insects = 1; low densities, but insects present = 2; moderate infestation, insects present and patchy throughout the site = 3; feeding damage frequent with high moth presence = 4; and abundant populations and damage (brown outs) = 5. We then used a linear regression analysis to evaluate the relationship between release size and infestation score.
We recovered N. conspurcatalis in or adjacent to the site at all release points except Everglades National Park (Table 1). The single release made at Everglades National Park was conducted hurriedly due to thunderstorm activity during the release (H. Cooley, pers. com). An additional release made at Corbett National Wildlife Refuge was omitted from the analysis because the L. microphyllum in the release site was treated with herbicide. We found no significant linear relationship between release size and infestation score (P = 0.06). However all releases of 4,000 or more larvae successfully established populations that persisted for at least 5 years, and at many sites, releases of 2,200 larvae were adequate to establish persistent populations.
Neomusotima conspurcatalis occupies isolated, though large, areas within the Old World climbing fern range in Florida. Currently N. conspurcatalis does not extend beyond Central Florida, but warming temperatures and fewer frost events may facilitate a northward range expansion. Notwithstanding extenuating circumstances, all populations have persisted for at least 5 years. Despite cold temperatures and the acquisition of parasitoids (Boughton et al. 2012b), our findings indicate that N. conspurcatalis and the Lygodium galling mite, Floracarus perrepae, are more widely distributed in greater abundances than previously understood (Boughton & Pemberton 2011, Lake et al. in press). Further investigations will evaluate the impact of N. conspurcatalis on L. microphyllum as well as determine the northern limits for N. conspurcatalis and future L. microphyllum control candidates.
We thank L. Jameson and C. Mason and the Arthur R. Marshall Loxahatchee National Wildlife Refuge for providing an airboat and other support to resurvey release sites. We also thank L. Rodgers and other representatives of the South Florida Water Management District for ongoing support for L. microphyllum biocontrol projects. H. Cooley of Everglades National Park facilitated helicopter transportation for sites within ENP. T. Center, G. Witkus and T. Wasylik (USDA-ARS, Invasive Plant Research Laboratory) were instrumental to relocating release sites and detecting agents in the field.
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MELISSA C. SMITH (1), *, ELLEN C. LAKE (1), PAUL D. PRATT (1), ANTHONY J. BOUGHTON (2) AND ROBERT W. PEMBERTON (3)
(1) USDA-ARS Invasive Plant Research Laboratory, 3225 College Avenue, Fort Lauderdale, FL 33314
(2) University of Florida, Tropical Research & Education Center, Homestead, FL 33031
(3) Research Associate, Florida Museum of Natural History; USDA-Agricultural Research Service (retired)
* Corresponding author: E-mail: Melissa.firstname.lastname@example.org
TABLE 1. RELEASE HISTORY, FEEDING SCORE AND DATE OF LAST ASSESSMENT FOR N. CONSPURCATALIS. SITES WITH (*) DENOTE THAT THEY WERE SPRAYED WITH HERBICIDE AND WERE NOT USED IN THE REGRESSION ANALYSIS. FEEDING LEVELS ARE SCORED AS FOLLOWS: 0, NO FEEDING SIGNS; 1, SIGNS OF OLD FEEDING; 2, LOW DENSITIES, BUT INSECTS PRESENT; 3, INSECTS PRESENT, BUT PATCHY THROUGHOUT THE SITE; 4, FEEDING DAMAGE FREQUENT WITH HIGH MOTH PRESENCE; AND 5, EXTENSIVE FEEDING DAMAGE AND POPULATION EXPLOSIONS (BROWN OUTS). WITH THE EXCEPTION OF RODGER'S RIVER IN EVERGLADES NATIONAL PARK AND TWO ISOLATED TREE ISLANDS IN LNWR, N. CONSPURCATALIS ESTABLISHED POPULATIONS AT ALL SITES. Location Site Name Release Date(s) Everglades National Rodger's 13-May-09 Park River, Cape Sable Jonathan Dickinson JD24 22 May 2008-21 July 2010 State Park Jonathan Dickinson JD25 31 March 2008-7 May 2008 State Park Jonathan Dickinson JD44 31 Jan 2008-23 Aug 2010 State Park JW Corbett National Corbett55 15-May-09 Wildlife Refuge * Lennar County Lennar2 24 July 2008-28 Aug 2008 Preserve Loxahatchee National Lox kiosk 28-Oct-09 Wildlife Refuge * Loxahatchee National Lox12 New 28-Oct-09 Wildlife Refuge * Loxahatchee National Lox32 29 Feb 2008-5 Dec 2008 Wildlife Refuge Strazzulla Loxahatchee National Lox41 27-Mar-09 Wildlife Refuge Loxahatchee National Lox42 27-Mar-09 Wildlife Refuge Loxahatchee National Lox43 27-Mar-09 Wildlife Refuge Loxahatchee National Lox44 27-Mar-09 Wildlife Refuge Loxahatchee National Lox5 10-Oct-08 Wildlife Refuge Cypress Creek Preserve Cypress 2 April 2009-10 Nov 2010 --SFWMD Creek Kissimmee River Kissimmee 2-Apr-09 --SFWMD River 1 Flatword Swamp Flatford 31 Aug 2009-11 Aug 2010 --SFWMD Swamp 1 Flatword Swamp Flatford 32 Aug 2009-11 Aug 2010 --SFWMD Swamp 3 Location Total Feeding Date last Score assessed Everglades National 4050 0 13-Dec-12 Park Jonathan Dickinson 17100 3 31-Jan-13 State Park Jonathan Dickinson 14791 3 29-Jan-13 State Park Jonathan Dickinson 2750 2 31-Jan-13 State Park JW Corbett National 4250 sprayed 26-Mar-13 Wildlife Refuge * Lennar County 13358 2 31-Jan-13 Preserve Loxahatchee National 2000 sprayed 13-Feb-13 Wildlife Refuge * Loxahatchee National 2000 sprayed 13-Feb-13 Wildlife Refuge * Loxahatchee National 19289 2 13-Feb-13 Wildlife Refuge Loxahatchee National 2200 2 10-Oct-12 Wildlife Refuge Loxahatchee National 2200 2 10-Oct-12 Wildlife Refuge Loxahatchee National 2200 0 10-Oct-12 Wildlife Refuge Loxahatchee National 2200 0 10-Oct-12 Wildlife Refuge Loxahatchee National 4400 2 13-Feb-13 Wildlife Refuge Cypress Creek Preserve 59209 3 5-Feb-13 --SFWMD Kissimmee River 14821 4 23-Oct-12 --SFWMD Flatword Swamp 12000 2 6-Mar-13 --SFWMD Flatword Swamp 12000 2 6-Mar-13 --SFWMD
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|Title Annotation:||Scientific Notes|
|Author:||Smith, Melissa C.; Lake, Ellen C.; Pratt, Paul D.; Boughton, Anthony J.; Pemberton, Robert W.|
|Date:||Jun 1, 2014|
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