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Biotic interference, especially by generalist predators, has been implicated in preventing establishment or limiting the impact of introduced weed biological control agents (Goeden & Louda 1976). Boreioglycaspis melaleuca e Moore (Homoptera: Psyllidae) was released into Florida in 2002 as part of a classical biological control program targeting the ecological weed Melaleuca quinquenervia (Cav.) S. T. Blake (‘melaleuca’) and is now established and contributing to the suppression of melaleuca (Tipping et al. 2008). The multicolored Asian lady beetle, Harmonia axyridis (Pallas) (Coleoptera: Coccinellidae) was introduced numerous times into the U.S. starting in 1916 as a biological control agent of Homoptera (Gordon 1985). Chapin & Brou (1991) first documented established populations in 1988 in Louisiana and Georgia. It appeared in Florida in the early 1990s where it feeds on soft scales, mealybugs, psyllids, whitefly larvae, and the eggs of Coleoptera and Lepidoptera (Michaud 2002). In 2007, we observed large populations of H. axyridis adults and larvae on melaleuca infested with B. melaleucae in our research plots at the USDA-ARS Invasive Plant Research Laboratory (IPRL) in Ft. Lauderdale, Florida (N 26°05’ W 80°14’) . Although other predacious coccinellids were present including Brachiacantha decora Casey, Coleophora inaequalis (F.), and Olla v-nigrum (Mulsant), H. axyridis is considered a dominant intraguild species and has outcompeted many coccinellid species (Pervez & Omkar 2006). Our objective was to determine if H. axyridis would attack and sustain itself on B. melaleucae under laboratory conditions. Adult H. axyridis were collected from melaleuca growing at IPRL and provisioned with B. melaleucae nymphs in the laboratory until they oviposited. Individual egg masses were incubated at 27°C until larval emergence. First instars ( n = 27) were confined in individual plastic containers (30 mL) with plastic snap lids along with a single melaleuca leaf containing various numbers of small (instars 1-3) and large (instars 4-5) of B. melaleucae in situ . This was done in lieu of transferring exact numbers because the nymphs are extremely delicate and easily injured or killed when handled. We strove to find leaves with similar numbers of small and large psyllids whose numbers we increased steadily as the H. axyridis larvae grew. For example, an average of 3 small and 1.5 large nymphs were added daily for first instar H. axyridis while fourth instars received 30.5 small and 14 large nymphs daily. Increases in provisioning were guided by the presence of surviving nymphs, which indicated that prey numbers were not limiting. Moisture was supplied with a moistened dental wick placed in the bottom of the container. Dead or missing nymphs were tallied every 13 d and a fresh leaf with their associated nymphs was added. Missing nymphs were assumed to have been consumed. Larval testing ended when H. axyridis died or pupated. Adult feeding trials were conducted for 7 d in the same manner with 12 adults that eclosed successfully from the larval feeding trials. Larvae and adults fed readily on B. melaleucae (Table 1) . However, the mean (±SE) larval development time was 23.0 ± 0.6 d, which may indicate that the psyllid is not an optimal food source when compared to other prey. For example, H. axyridis completed larval development in 11.2 d when fed fresh eggs of Sitotroga cerealella (Olivier) (Abdel-Salam & Abdel-Baky 2001), 10.5 d when fed Myzus persicae (Sulzer) (Lanzoni et al. 2004), and 9.6 d when fed Aphis pisum Harris (Specty et al. 2003).

An Introduced Insect Biological Control Agent Preys on an Introduced Weed Biological Control Agent