The neotropical bee Centris nitida Smith has naturalized in southeastern Florida and in Sarasota on the Gulf coast. This furry yellow and black bee has been confused with the closely related C. lanosa Cresson, a native bee restricted to northern Florida and the American Southwest and adjacent Mexico. Female C. nitida are smaller than those of both C. lanosa and C. errans Fox, a furry brown-colored native Centris which is sympatric with C. nitida in southern Florida. The 3 Centris bees now occurring in Florida are readily separated by their distinctive facial markings. Female C. nitida have a vertical black line in the middle of the clypeus. Centris nitida is a polylectic, oil-collecting bee observed to visit flowers of 28 species in 10 plant families, including 8 oil reward flower species in the Malpighiaceae, and 10 species of buzz pollinated flowers in the Fabaceae and Solanaceae in Florida. Centris nitida may have environmental impacts through pollination of selected native, ornamental and invasive plants, as well possible competition with the sympatric native C. errans through common usage of oil reward flowers.
The genus Centris (Apidae: Centridini) contains about 144 species of bees which are Neotropical in distribution, except for few species ranging into the Neartic and Araucarian regions (Michener 2000). Many female Centris species are highly specialized collectors of floral oils, which they use to provision their brood and/or in the construction of their nest cells (Simpson et al. 1977; Buchmann 1987). The few Centris species that occur in the United States are limited to warm climate areas of the Southwest and Florida (Snelling 1984). Florida has 2 native Centris spp.: C. errans, formerly C. versicolor (F.) and often cited as such (Snelling 1984), and C. lanosa (Mitchell 1962; Snelling 1984). In this paper, we report the naturalization of C. nitida Smith, a tropical American species, which now appears to be common and widespread in southeastern Florida and in Sarasota on the Gulf coast. We describe the circumstances in which we discovered the occurrence of C. nitida in Florida. Centris nitida occurs widely in tropical America, with South American collections (Ecuador and Columbia), Central America (Belize, Costa Rica, Honduras, and El Salvador), and numerous collections from many parts of Mexico (Snelling 1984). Droege et al. (2007) adds collections from Peru and Bolivia, and single 1985 Ricon Mountains, Pima Co., Arizona collection by Minckley (Droege et al. 2007). There may be some uncertainty about this Arizona occurrence because Snelling (1984) indicated that previous Arizona collections identified as C. confinis (Perez), a synonym of C. nitida, were misidentified.
Material and Methods
Centris nitida’s native range was determined from collection data from specimens in the Snow Entomology Museum Collection, University of Kansas, and the American Museum of Natural History, New York, and posted on the Discover Life Website (Droege et al. 2007) and Snelling (1984). We illustrated the differences in facial color patterns of C. nitida and Florida’s 2 native Centris with a photomontage system at the Florida Department of Agriculture and Consumer Services in Gainesville. To quantify size differences in these bees, we made measurements on specimens of C. nitida that we collected in Broward and Miami-Dade Counties, and of C. lanosa and C. errans from the Florida State Collection of Arthropods (FSCA) (Table 1). We also measured the 2 specimens of male C. nitida that were available at the FSCA to increase the sample size. Using a dissecting microscope, we measured the width of the dorsal surface of the thorax inclusive of the wing inserts, the length of the thorax, and the length of the abdomen. We summed the 2 measures of length and then multiplied that by the thorax width to obtain body sizes for the 3 species. We used One-Way ANOVA to determine the differences in body size among the 3 species. Bonferroni tests were used for post hoc pairwise comparisons. Male and female bees were analyzed separately. All statistical analyses were carried out with SPSS 13.0 (SPSS, Inc., Chicago).
Furthermore, we clarified the confusion surrounding the distribution of C. lanosa in Florida based on information in Snelling (1984), from J. Neff (University of Texas, Austin), and collection data of all C. lanosa specimens from various sources that we examined. In addition, we determined the distribution and the activity period for C. nitida from multiple information sources. Firstly, one of us (RWP) made observations on C. nitida in a Broward residential yard with a diverse flowering species including oil flowers from Sep 2004 to Jul 2006, during which time the bee was presumed to be C. lanosa. Secondly, we made observations and collections frequently in 2 residential gardens, 1 mentioned above, the other in Miami-Dade County, which harbored 15 plants of Brysonima lucida Rich. Ex Kunrh. (Malpighiaceae), a native oil reward flower species, during Mar to Sep 2007, after the identity of C. nitida became clear to us. Thirdly, we made 5 observation and collection trips to 5 rocky pinelands, the prime habitat for B. lucida, during Mar to May 2007, the peak flowering period of B. lucida in Miami-Dade and Monroe Counties, and 7 trips to the Fairchild Tropical Botanic Garden in Miami-Dade, where several large plants of B. lucida and many introduced species of oil reward flowers were planted. Fourthly, from Mar to Sep 2007 we visited Home Depot home improvement stores in Broward, Miami-Dade, Monroe, Martin, and Palm Beach Counties in southern Florida, and in Orlando, Orange County, in central Florida to observe whether or not C. nitida was present on the floral displays of Angelonia angustifolia Benth. (Scrophulariaceae), a popular ornamental plant with oil reward flowers. Because C. nitida predictably used A. angustifolia at the Home Depot stores in Broward and Miami-Dade Counties where the bee was known to be present, we used the Home Depot visits as a supplemental indicator of the bee’s presence or absence elsewhere. We also determined the distribution and activity period for C. errans based on our observations and collections during the same periods mentioned above. Finally, we summarized host plant information of the sympatric C. errans and C. nitida. Representative specimens of both bees will be placed in the Florida State Collection of Arthropods in Gainesville, the American Museum of Natural History in New York, and the Snow Entomology Museum Collection, University of Kansas in Lawrence.
Discovery of C. nitida in Southern Florida
We first encountered C. nitida in Ft. Lauderdale, Broward County in southeastern Florida in 2004, while making observations of the recently naturalized orchid bee Euglossa viridissima Friese (Pemberton & Wheeler 2006). Both the orchid bee and C. nitida were commonly seen collecting (buzzing) pollen from the flowers of cultivated Senna and some Solanum species. Centris nitida also was observed collecting oil from the flowers of the cultivated native B. lucida in the same residential garden in Ft. Lauderdale. This bee was presumed to be C. lanosa, a similar-sized black and yellow species known to occur in Florida (Mitchell 1962), and reported from Miami-Dade County (Pascarella et al. 1999; Pascarella 2007). However, attempts to confirm the bee’s identity with the keys in Mitchell (1962) and the keys in Pascarella (2007)--his Bees of Florida website (based on Mitchell’s keys) failed. The bee was subsequently successfully keyed as C. nitida with the Centris key on Discover Life website (Droege et al. 2007). Correspondence with S. Droege, the lead author of the Discover Life Apoideae section (along with S. Kolski, J. Ascher, and J. Pickering), indicated that the inclusion of C. nitida in the key as a species known from Florida, was based on his collection of 2 male C. nitida along a Palm Beach County, Florida canal on Jan 26, 2005. Those bees were identified by John Ascher, who compared them to specimens in the American Museum of Natural History collection.
We examined the 2 specimens included in the Pascarella’s 1999 paper and website (2007) records for C. lanosa in Miami-Dade County, and found them both to be C. nitida. These specimens (housed in the K. Waddington laboratory, Department of Biological Sciences, University of Miami) were collected at the Fairchild Tropical Botanic Garden and the University of Miami, Coral Gables in 1997 and identified by J. Pascarella. These specimens constitute the earliest known collections of C. nitida in Florida and the eastern United States. We also examined “C. lanosa” specimens collected a year later in 1998 by Suzanne Koptur in the Rockdale Pineland, Miami-Dade County. We determined that these specimens (housed in the Koptur Laboratory at Florida International University, Miami) also are C. nitida. These early collection sites, the Rockdale Pineland and the University of Miami, are ca. 11 km apart, so it appears that C. nitida was already relatively widespread within southeastern Miami-Dade County by 1998, occurring in both urban garden and natural environments. The misidentifications were due to C. nitida’s resemblance to C. lanosa (both are robust black and yellow medium sized furry bees) and probably to Michell (1962) listing C. lanosa’s distribution simply as Florida.
Distinguishing the 3 Centris Bees in Florida
While C. nitida’s yellow and black furry appearance resembles that of C. lanosa, this coloration distinguishes C. nitida from C. errans, which is furry brown. The color patterns of the faces of the 3 Centris bees differ markedly (Fig. 1). The black vertical line on the mostly cream colored clypeus of the face of female C. nitida readily separates it from the female of C. lanosa, which has a black face with a light colored band in the center just below the antennal insertions, and the female of C. errans, which has a black face with a white inverted “T” on the clypeus at the base. The faces of the males of these Centris species are yellow marked with black in distinctive patterns that separate them from each other and the females (Fig. 1).
The 3 bees also differed statistically in body size (Between groups MS = 407.57, F2, 20 = 14.17, P < 0.001,). Females of C. nitida were smaller than females of both C. errans and C. lanosa (Bonferroni tests, Table 1). Males of the 3 Centris species, however, were not significantly different (Between groups MS = 65.30, F2, 20 = 1.43, P = 0.263, one-way ANOVA, Table 1).
Centris nitida Specimens Collected in Florida
Mar: 1♂ perched next to Cyrtopodium punctatum (L.) Lindl. plant, 4 III 2007, Ft. Lauderdale, FL, RW Pemberton; 1♀ on Cyrtopodium punctatum flowers, Fairchild Tropical Botanic Garden, Coral Gables, FL, 16 III 2007, H. Liu and R.W. Pemberton; 8♀ on Byrsonima lucida flowers, 23 III 2007, Kendall Lakes, Miami-Dade Co. FL, H. Liu; 4♀ on Brysonima lucida flowers, 25 III 2007, Ft. Lauderdale, R.W. Pemberton; 1♀ on Suessenguthia multisetosa (Rusby) Wassh. & J.R.I.Wood flowers, 25 III 2007, Ft. Lauderdale, FL, R.W. Pemberton; 2♀ on Cyrtopodium punctatum flowers, 25 III 2007, Ft. Lauderdale, FL, R.W. Pemberton; 1♀ on Byrsonima lucida flowers, 25 III 2007, Kendall Lakes, Miami-Dade FL, H. Liu; 1♀ on Byrsonima lucida flowers, 27 III 2007, Kendall Lakes, Miami-Dade FL, H. Liu; 1♀ on Byrsonima lucida flowers, 31 III 2007, Kendall Lakes, Miami-Dade Co. FL, H. Liu. 1♀ on Cyrtopodium punctatum flowers, 31 III 2007, Fairchild Tropical Botanic Garden, Coral Gables, FL, R.W. Pemberton and H. Liu. Apr: 3♀ on Angelonia angustifolia flowers, 1 IV 2007, Ft. Lauderdale, FL, R.W. Pemberton; 1♀ on Oncidium sphacelatum Lindl. flowers, 5 IV 2007, Ft. Lauderdale, FL, R.W. Pemberton; 2♀ on Malpighia emarginata DC. flowers, 1♂ on Malpighia emarginata leaf, 6 IV 2007, Davie, FL, R.W. Pemberton; 1♀ on Angelonia angustifolia flowers, 1♂ near Angelonia angustifolia flowers, 7 IV 2007, Ft. Lauderdale, FL, R.W. Pemberton; 2♀ on Malpighia coccigera flowers, 7 IV 2007, Davie, FL, R.W. Pemberton; 1♀ on Malpighia “punicea” flowers, 7 IV 2007, Davie, FL, R.W. Pemberton; 2♂ on Bunchosia armeniaca DC. flowers, 18 IV 2007, Davie, FL, R.W. Pemberton; 18 IV 2007, Davie, FL, R.W. Pemberton; 1♂ Malpighia emarginata flowers, 1♂ on Parkinsonia aculeata L. flowers, 28 IV 2007, West Palm Beach, FL, R.W. Pemberton. May: 1♀ on Byrsonima lucida flowers, 11 V 2007, Ft. Lauderdale, FL. R.W. Pemberton; 1♀ on Brysonima lucida flowers, 1♂ on Brysonima lucida flowers, 10 V 2007, Ft. Lauderdale, FL, R.W. Pemberton; 1♀ on Malpighia emarginata flowers, 10 V 2007, Kendall Lakes, Miami-Dade Co. FL, H. Liu; 1♂ perched near Cyrtopodium polyphyllum (Vell.) Pabst ex F. Barrios, 19 V 2007, Ft. Lauderdale, FL, R.W. Pemberton, 1♀ on Cyrtopodium polyphyllum, 23 V 2007, Boystown Pineland Park, Miami-Dade Co. FL, H. Liu & R.W. Pemberton. June: 1♀ on Cyrtopodium polyphyllum flowers, 6 VI 2007, Kendall Lakes, Miami-Dade Co. FL, Q. Liu; 1♀ on Cyrtopodium polyphyllum flowers, 7 VI 2007, Kendall Lakes, Miami-Dade Co. FL, Q. Liu. Aug: 1♀ on Senna alata (L.) Roxb. flowers, 22 V111 2007, Ft. Lauderdale, FL, R.W. Pemberton. Sep: 1♀ on Senna alata flowers, 23 IX 2007, Ft. Lauderdale, FL, R.W. Pemberton. Oct: 5♀ on Malpighia emarginata flowers, 1♀ on Senna ligustrina (L.) H.S. Irwin & Barneby flowers, 1 X 2007, Marie Selby Botanical Garden, Sarasota, FL, R.W. Pemberton. 1♀ on Senna mexicana (Jacq.) H.S. Irwin & Barneby flowers, 8 X 2007, Ft. Lauderdale, FL, R.W. Pemberton. Nov: 1♀ on Malpighia emarginata flowers, 1♂ near Malpighia emarginata, 3 XI 2007, Mounts Botanical Garden, Palm Beach County, FL, R.W. Pemberton. Dec: 1♀ on Senna alata flowers, 4 XII 2007, Fairchild Tropical Botanic Garden, Coral Gables, FL, H. Liu. January: 1♂ on Cuphea sp. flowers, 4♀ on Angelonia angustifolia flowers, 11 I 2008, Davie, FL, R.W. Pemberton. February: 1♂ on Cuphea sp. flowers, 1♀ on Angelonia angustifolia flowers, 2 II 2008, Davie, FL, R.W. Pemberton.
Other Collectors--1♀, 3♂, 1997, Fairchild Tropical Botanic Garden, Coral Cables FL, J. Pascarella; 1♀ on Calyptranthes pallens Griseb., 1997, Univ. Miami, Coral Cables, FL, J. Pascarella; 2♀ on Brysonima lucida flowers, 1 V 1998, Rockdale Pineland, Miami Dade, S. Koptur.
Centris errans Specimens Collected in Southern Florida
Mar: 2♀ on Cyrtopodium punctatum flowers, 16 III 2007, Fairchild Tropical Botanic Garden, Coral Gables, FL, R.W. Pemberton and H. Liu; 2♀ on Brysonima lucida flowers, 23 III 2007, Kendall Lakes, Miami-Dade Co. FL, H. Liu. Apr: 2♀ on Brysonima lucida flowers, 1 IV 2007, R.W. Pemberton and H. Liu, Navy Wells Pineland, Miami-Dade Co., FL, 3♀ on Brysonima lucida flowers, 14 IV 2007, Seminole Wayside Park, Homestead, FL, R.W. Pemberton. May: 1♀ on Brysonima lucida flowers, 6 V 2007, Ft. Lauderdale, FL, R.W. Pemberton; 1♀ on Brysonima lucida flowers, 1♀ on Stigmaphyllon sagraeanum A. Juss. flowers, 1♀ on Galphimia gracilis Bartl. flowers, 8 May 2007, Fairchild Tropical Botanic Garden, Coral Cables, FL, H. Liu and R.W. Pemberton; 1♀ on Brysonima lucida flowers, 28 V 2007, Boystown Pineland County Park, Miami-Dade Co., FL, H. Liu. Jun: 1♀ on potted Brysonima lucida flowers, 5 VI 2007, Boystown Pineland County Park, Miami-Dade Co., FL, H. Liu.
Distribution of Centris Species in Florida
Centris lanosa is restricted to the northern part of the state. We examined specimens of C. lanosa in the Florida Arthropod Collection, Gainesville and found they were from only 3 northern Florida counties (Alachua, Clay, and Gilchrist). These were the only specimens listed by Snelling (1984). Centris lanosa has a disjunct distribution occurring in Kansas, Texas, Oklahoma (Snelling 1984), and Arizona (J. Neff, pers. comm.), and then in northern Florida (Snelling 1984) and southern Georgia (J. Neff, pers. comm.), where its plant associate, Krameria lanceolata Torr. (Krameriaceae), occurs (J. Neff, pers. comm.). Krameria lanceolata, which has oil reward flowers gathered by females of C. lanosa to provision their brood, is absent from southern Florida (Wunderlin & Hansen 2003).
Our observations and collections indicate that C. nitida occurs in Miami-Dade, Broward, and Palm Beach Counties in southeastern Florida. We also collected this species on the Gulf coast in Sarasota about 60 km south of Tampa. The Sarasota collection site is ca. 260 km from the nearest collection site in southeastern Florida (West Palm Beach in Palm Beach County). Interestingly, the bees were commonly observed to gather oils from the flowers of potted plants of A. angustifolia at Home Depot stores in both Broward and Miami-Dade Counties. It was not unusual to see multiple bees foraging on the flowers of the potted plants in these stores at the same time. However, we did not observe C. nitida in a Monroe County Home Depot store, or in the Navy Wells Pineland natural area 2 km north of the Everglades National Park, or in the pinelands on Big Pine Key, Monroe County, when B. lucida was abundant and in peak bloom. Similarly, we did not detect C. nitida on A. angustifolia at the visited Home Depot stores in Martin or Orange Counties. This may indicate that C. nitida may not have yet reached the ENP, Monroe County, the southern most part of southern Florida, or north of Palm Beach County on the southeastern coast. Although one of the early collections of C. nitida was from the Rockdale pineland in 1998, our survey in pine rocklands did not locate the bee.
The specimen data for our C. errans collections indicate that this species has a larger geographic range, a greater number of floral species associations, and a longer activity period in Florida than previously understood. This bee was thought to be limited to the pine rockland habitats of Miami-Dade and Monroe Counties, where its native oil reward species, B. lucida, occurs (Pascarella 2007). We collected a single bee from the flowers of a cultivated B. lucida planted in a Ft. Lauderdale garden in Broward County, which is one county north of Miami-Dade County, and well beyond the natural range of the plant.
Centris nitida and Centris errans Floral Records in Florida
Centris nitida was observed visiting the flowers of 28 species in 10 different plant families to collect pollen, edible oil, and nectar (Table 2); the bee appears to be polylectic. Centris errans, by contrast, was observed to visit the flowers of only 5 species (Table 2). Females of both C. nitida and C. errans collect the edible oil rewards of flowers to provision their brood or construction of nests. Centris nitida was observed to visit 8 oil reward flower species in 5 genera of the Malpighiaceae; all but 1 were introduced ornamental plants, and a single species in the Schrophulariaceae, A. angustifolia, an introduced ornamental plant, native to South America (Table 2). Centris errans was observed to visit 3 oil reward flower species belonging to the Malpighiaceae, 2 of which were introduced ornamentals, whereas 1 is native to southern Florida (Table 2).
Females of both Centris species are able to buzz poricidal (opening by terminal pores) anthers of flowers to remove pollen. Centris nitida was observed to buzz flowers of 10 species of plants in the genera Exacum, Lycianthes, Senna and Solanum to collect pollen (Table 2), while C. errans was observed to buzz flowers of Chamaecrista keyensis (Liu & Koptur 2003). Territories of male C. nitida territories were observed on and around small Malpighia emarginata trees in 4 places in 3 counties. Male territories also were seen near potted plants of A. angustifolia, Galphimia gracilis (Malpighiaceae), and Cyrtopodium punctatum. Both C. nitida and C. errans visited orchid flowers (Table 2), but the details of these interactions (Pemberton & Liu, unpublished data) will be reported elsewhere.
Phenology of Centris nitida and C. errans in Florida
From 2004 to 2006, observations of adult C. nitida activity, in conjunction with studies of E. viridissima, indicate that C. nitida to be present during the months Apr, May, Jun, Jul, Sep, Oct, Nov, and Dec. Attempts to collect C. nitida in 2007 from Mar through Feb successfully located bees in every month, although they were more abundant in the spring and summer months.
We collected C. errans from Mar to Jun. The May and Jun collections were after the recognized adult activity period of Mar to Apr (Mitchell 1962).
Environmental impacts related to the naturalization of C. nitida may occur primarily through the bee’s pollination of selected native, ornamental, and invasive plants. Twenty two of the 28 species (78.6%) visited by C. nitida are introduced plants in Florida, 7 of these plants were naturalized, while 1, Senna pendula (L) Roxb., is a Category I invasive plant ( http://www.fleppc.org). The value of urban landscapes in providing the specialized flowers needed by native Centris has been recently discussed by Koptur (2006). However, introduced oil reward flower species in urban landscapes could promote mutualism with C. nitida and lead to increased abundance of these plants and the bee. Centris nitida appears to be polylectic because of the large number of plant species it visits. In contrast, the close association of C. errans with B. lucida coupled with our observations of the bee visiting only 2 other species of Malpighiaceae, suggests that it is oligolectic. Mitchell (1962), however, lists flower records for C. errans that include 5 additional genera and families: Borrichia (Asteraceae), Carambola (Oxalidaceae), Eugenia (Myrtaceae), Ocimum (Labiaceae), Securidaca (Polygalaceae).
It appears that C. nitida has a disjunct distribution, in southeastern Florida and in the Sarasota area of the west coast, 2 well separated areas. We do not know if C. nitida occurs between these areas. Surveys in Naples on southwest coast failed to detect the bee. The disjunct distribution raises the possibilities of 2 separate introductions of this bee to Florida. Alternatively, C. nitida could have been introduced to one area, and then subsequently spread or was moved to the other. Because C. nitida is known to nest within wood (Frankie et al. 1993), it may have been introduced as a nest within wood or hollow wooden objects. The recently introduced orchid bee (E. viridissima) also nests within enclosed spaces (Skov & Wiley 1995), which suggests that it may have also been imported as a nest(s). All but 1 of the 17 bees accidentally imported and established in North America live in hollow plant stems or other preformed cavities (Ascher 2001), supporting the idea that bees with this type of nests are more able to naturalize than bees that are ground nesters.
The occurrence of C. nitida in the Ricon Mountains, Pima County, Arizona appears to be in USDA Hardiness Zone 9 ( http://www.cobraplant.com/Zone.GIF). The distribution of C. nitida in southeastern Florida is within USDA Hardiness Zone 10b. Zone 9 occupies the northern 2/3 of the Florida peninsula, extending to the Georgia border along the east coast and almost to Cedar Key on the west coast of Florida. If C. nitida is dependent on oil reward flowers, it would need to use the flowers of ornamental members of the Malpighiaceae or the common ornamental herb A. angustifolia, which it already uses in southern and southwestern Florida, to extend northward. The bee already occurs in Broward, Palm Beach, and Sarasota Counties, north of the distribution of B. lucida, the only oil reward flower plant native to southern Florida. When it reaches the central and northern Florida peninsula, it could encounter K. lanceolata, another native plant with oil reward flowers. As mentioned above, this plant fosters the presence of C. lanosa in both northern Florida and in Texas and Arizona. Although not detected in this study, C. nitida could spread into the Everglades National Park and in the Florida Keys (Monroe County), where B. lucida is abundant in understory of the rocky pinelands. Only a single C. nitida was detected in the surveyed rocky pinelands in this study, although it was previously collected in an urban rocky pineland in 1998 (as C. lanosa) by S. Koptur. This bee was commonly encountered in urban gardens and parks and this contrast suggest that C. nitida may continue to have a greater presence in human habitats than natural areas, which have fewer floral resources for the bee.
The naturalization of C. nitida in southern Florida and its potential spread to northern Florida creates the possibility of competition between this exotic bee and Florida’s 2 native Centris. Both exploitative and interference competition have been suggested in introduced honey bee-native bee interactions (Gross & Mackay 1998; DuPont et al. 2004), and both types of competition could be involved here. There is overlap in floral oil reward plant species used by C. nitida and the native C. errans in southern Florida, as well as geographic sympatry in Broward and Miami-Dade Counties. We have observed both species to forage at the same time on B. lucida flowers in Miami-Dade County but did not observe aggression or apparent physical inference. Larger body size may favor C. errans over C. nitida in direct contact (interference competition), but the apparent greater abundance of C. nitida may favor it over C. errans in exploitative competition.
If C. nitida spreads into the range of C. lanosa in northern Florida, the 2 bees may compete for the resources of K. lanceolata. Competition for nest sites between C. nitida and the native Centris will not occur. Centris lanosa and C. errans belong to subgeneric taxa (subgenus Centris and subgenus Paracentris) in which all members nest in the ground (J. Neff, pers. comm.), while C. nitida is reported to nest in wood (Frankie et al. 1993). Food resource competition with non-Centris bees is unlikely to occur for floral oils but might occur for pollen and nectar flowers and for nest sites between C. nitida and other wood nesters such as some megachilid bees.
In the limited interaction involving C. nitida and the orchid bee (E. viridissima) some bumping has been observed among bees at the flowers of Senna species with poricidal dehiscent anthers, but the bees appeared to be only momentarily deflected from foraging. Because these tropical bees have naturalized in subtropical southern and southwestern Florida relatively recently, their long-term persistence, environmental interactions, and impacts are unknown. The outcomes of potential competition between C. nitida, E. viridissima and other bees in Florida also will depend on their foraging patterns in relationship to resource availability (Schaffer et al. 1979). More studies are needed to understand the impacts of these newly naturalized solitary bees on Florida’s environments.
Although naturalized bees are relatively rare compared to naturalized plants, increasing numbers of exotic bees are being detected in temperate North America (Ascher 2001). Until recently only 3 exotic bees, Apis mellifera L., Megachile lanata (Fabricius) and M. concinna Smith, were known from Florida (Deyrup et al. 2002). With the recent naturalizations of E. viridissima (Pemberton & Wheeler 2006) and C. nitida the number of exotic bees in Florida has almost doubled.
We thank S. Droege for information about his collection of C. nitida in Palm Beach Co. FL; J. Pascarella and K. Waddington for discussion and access to specimens housed at the University of Miami, S. Koptur for access to specimens she collected in Miami-Dade County, and J. Neff provided information about C. lanosa’s disjunct distribution and dependence on Krameria lanceolata. We thank P. Skelley, who kindly took photographs of Centris specimens with the photomontage system at Florida Department of Agriculture and Consumer Services, which we also thank. We thank F. W. Howard for translating the abstract into Spanish.
- J. S. Ascher 2001. Hylaeus hyalinatus Smith, a European bee new to North America, with notes on other adventive bees (Hymenoptera: Apoidea). Proc. Entomol. Soc. Wash 103:184–190. Google Scholar
- S. L. Buchmann 1987. The ecology of oil flowers and their bees. Annu. Rev. Ecol. Syst 18:343–369. Google Scholar
- G. W. Frankie, S. B. Vinson, L. E. Newstrom, and J. F. Barthell . 1988. Nest site and habitat preferences of Centris bees in the Costa Rican Dry Forest. Biotropica 20:301–310. Google Scholar
- M. Deyrup, E. Jayanthi, and B. Norden . 2002. The diversity and floral hosts of bees at the Archbold Biological Station, Florida (Hymenoptera: Apoidea). Insecta Mundi 16:87–120. Google Scholar
- S. Droege, S. Kolski, J. Ascher, and J. Pickering . 2007. Apoideae, Discover Life website. (http://www.discoverlife.org). Google Scholar
- Y. L. DuPont, D. M. Hansen, A. Valido, and J. M. Olesen . 2004. Impact of introduced honey bees on native pollination interactions of the endemic Echium wildpretii (Boraginaceae) on Tenerife, Canary Islands. Biol. Conserv 118:301–311. Google Scholar
- C. L. Gross and D. Mackay . 1998. Honeybees reduce fitness in the pioneer shrub Melastoma affine (Melastomataceae). Biol. Conserv 86:169–178. Google Scholar
- S. Koptur 2006. The conservation of specialized and generalized pollination systems in subtropical ecosystems: a case study. In Ch. 15 in N. Waser and J. Ollerton [eds.], Specialization and Generalization in Plant-pollinator Interactions. University of Chicago Press, Chicago, Illinois. Google Scholar
- H. Liu and S. Koptur . 2003. Breeding system and pollination of a narrowly endemic herb of the Lower Florida Keys: impacts of the urban wildland interface. American J. Bot 90:1180–1187. Google Scholar
- C. D. Michener 2000. The Bees of the World. John Hopkins University Press, Baltimore, Maryland. Google Scholar
- T. B. Mitchell 1962. Bees of the Eastern United States. Vol. 2. North Carolina Ag. Exp. Sta. Tech. Bull. 152: 1-556. Google Scholar
- J. B. Pascarella, K. D. Waddington, and P. R. Neal . 1999. The bee fauna (Hymenoptera: Apoidea) of Everglades National Park. Florida and adjacent areas: distribution, phenology, and biogeography. J. Kansas Entomol. Soc 72:32–45. Google Scholar
- J. Pascarella 2007. Bees of Florida. (http://chiron.valdosta.edu/jbpascar/Intro.htm). Google Scholar
- R. W. Pemberton and G. S. Wheeler . 2006. Orchid bees don’t need orchids, evidence from the naturalization of an orchid bee in Florida. Ecol 87:1995–2001. Google Scholar
- W. M. Schaffer, D. B. Jensen, D. E. Hobbs, J. Gurevitch, J. R. Todd, and M. V. Schaffer . 1979. Competition, foraging energetics, and the cost of sociality in three species of bees. Ecol 60:976–987. Google Scholar
- B. B. Simpson, J. L. Neff, and D. L. Seigler . 1977. Krameria, free fatty acids and oil-collecting bees. Nature 267:150–151. Google Scholar
- C. Skov and J. Wiley . 2005. Establishment of the Neotropical orchid bee Euglossa viridissima (Hymenoptera: Apidae) in Florida Florida Entomol 88:225–227. Google Scholar
- R. Snelling 1984. Studies on the Taxonomy and Distributions of American Centriidine Bees (Hymenoptera: Anthophoridae). Contrib. Sci. No. 437:1–69. Google Scholar
- R. P. Wunderlin and B. F. Hansen . 2003. Guide to the Vascular Plants of Florida. Second Edition, University Press Florida, Gainesville. Google Scholar
Centris species body size (thorax length + abdomen length) × thorax width (mm2) comparison. Six of the 8 males and all females of C. nitida were collected from southern Florida, and all other specimens were sampled from the collection of the Florida State Museum of Arthropods. Different letters indicate a statistical difference in body size of different species.
Flower species visited by Centris nitida and C. errans in southern Florida. Observations are the authors except where indicated by footnotes. Native species are in bold, and naturalized species are underlined. Interactions with orchid species will be discussed in detail elsewhere.