JHR 37: 127-135 (2014) oe JOURNAL OF | *0eerreieved opencoss ural doi: 10.3897/JHR.37.708 | SHORT COMMUNICATION (MEE Hymenopter a www.pensoft.net/journals/jhr The imernaonl Sociey of Hymenopexriss, RESEARCH Parasitoid wasps from three Jamaican localities: A pilot study Fadia S. Ceccarelli', Dwight E. Robinson’, Hans Clebsch?, Alejandro Zaldivar-Riverén' I Coleccién Nacional de Insectos, Instituto de Biologta, Universidad Nacional Auténoma de México, 3er. circuito exterior s/n, Cd. Universitaria, Copilco Coyoacan, A. P 70-233, C. P 04510., D. E, México 2 Department of Life Sciences, University of the West Indies, Mona, Kingston 7, Jamaica. 3 Department of Invertebrate Zoology, Cleveland Museum of Natural History, 1 Wade Oval Circle, Cleveland, OH, USA Corresponding author: Fadia S. Ceccarelli (saracecca@hotmail.com) Academic editor: G. Broad | Received 19 January 2014 | Accepted 3 March 2014 | Published 28 March 2014 Citation: Ceccarelli FS, Robinson DE, Clebsch H, Zaldivar-Riverén A (2014) Parasitoid wasps from three Jamaican localities: A pilot study. Journal of Hymenoptera Research 37: 127-135. doi: 10.3897/JHR.37.7081 Abstract Parasitoid wasps are an extremely speciose, ecologically and economically crucial group of insects. Despite this, they have received disproportionally little attention from scientists, in particular in certain areas of the world. One such area is the Caribbean, where studies are scarce despite the importance of parasitoid wasps, and the uniqueness and diversity of the Caribbean islands. To verify whether an adequate diversity of parasitoid wasps at family level can be found to warrant future studies, this study carries out prelimi- nary sampling in three localities in Jamaica. A total of 1522 individual parasitoid wasps, belonging to at least 16 different families collected during 16 events provide preliminary evidence there is in fact a high diversity of parasitoid wasps in Jamaica, and that future studies there, as in the rest of the Caribbean are definitely worthwhile. Keywords Caribbean, biodiversity, parasitoids Copyright Fadia S. Ceccarelli et al. This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited. 128 Fadia S. Ceccarelli et al. / Journal of Hymenoptera Research 37: 127-135 (2014) Introduction Parasitoids are organisms that spend part of their life cycle feeding on or inside a host, eventually killing it. This lifestyle has been adopted by a notable number of insects, and in Hymenoptera approximately 80% of its species are parasitoids (LaSalle and Gauld 1991, Quicke 1997). Parasitoid wasps are widespread and highly abundant, playing an important role not only in ecosystem balancing, but also in biological crop pest control and conservation planning via biodiversity surveys (LaSalle and Gauld 1991, Eggleton and Belshaw 1992, Lewis and Whitfield 1999). Despite their great importance, these wasps are poorly studied. In fact, it has been estimated that even though there are ap- proximately 17,000 described species belonging to the family Braconidae, the total number of species has been estimated at approximately 42,653 (Jones et al. 2009) or between 30,873 and 50,886 (Dolphin and Quicke 2001). In addition to a dire need for taxonomic work on parasitoid wasps, there is an even greater scarcity of studies on their biology and ecology. The islands of the Caribbean Sea represent a highly interesting part of the world, since they are of complex and varying geological origins: some are volcanic, some tec- tonic and others continental (Burke 1988, van Benthem et al. 2013). These islands are therefore interesting from a biogeographical perspective as well. To carry out biogeo- graphic as well as other biological and ecological studies of this region, it is necessary to first be familiar with the flora and fauna of these islands. While certain islands are well-studied for select taxa such as anolis lizards (e.g. Losos and Schluter 2000, Ord et al. 2013), there are several taxa on Caribbean islands that are still largely unexplored. For example, parasitoid wasps in Jamaica are definitely understudied, where some of the few existing works include agriculture-related studies of parasitoid wasps as natu- ral enemies of crop pests (e.g. Alam 1990), or taxonomic studies (e.g. Martinez et al. 2012). The fact that such few studies exist is unfortunate considering the ecological importance of the taxon in question, and the exceptional geographical location and topology of Jamaica. In this study we set out to verify whether collecting efforts in Jamaica would yield high numbers of parasitoid wasps to warrant more detailed future studies, using two of the most common collecting techniques for parasitoid wasps, namely yellow pan trapping (YPT) and sweep netting (e.g. Noyes 1989, Missa et al. 2009, Abrahamczyk et al. 2010). We present preliminary data to show that sampling of parasitoid wasps in the Caribbean islands in general, and Jamaica in particular, is worthwhile for future studies of agriculture, ecology, conservation, systematics and biogeography. Materials and methods Parasitoid wasps for this study were collected during the month of November 2010. Three localities were chosen in the Jamaican parishes of St. Andrew, St. Mary and Trel- awny (see Figure 1). Within these localities, a total of 16 collecting events took place, Parasitoid wasps from three Jamaican localities: A pilot study PAS) 4 or “J os at Aer Bodh Atlantic a Ocean Pacific Ocean Poy ;00gleearth Cc Locality 2 Figure |. Maps and habitat photographs. Maps in the centre of the figure showing the geographic position of the three localities sampled in this study with surrounding photographs of the habitat types. Numbers in circles represent the collection code as shown in Table 1 without the JAM prefix. either using a sweep net, or setting yellow pan traps (YPT) (for details see Table 1). The three localities, as well as each collecting event within the localities differed in general habitat type, vegetation cover, topology and climatic conditions, all of which were considered when interpreting the results. More specifically, locality 1 comprised an area of approximately 0.90 square kilo- metres (km?) (221.31 acres) in a mountainous area (Blue Mountains), at elevations ranging from 860 to 1205 metres above sea level (m.a.s.l.) As such, most of the col- lecting sites were on slopes, and the area overall consisted of small patches of primary forest, mostly highly fragmented by human activity. Collecting events JAMO1 and 130 Fadia S. Ceccarelli et al. / Journal of Hymenoptera Research 37: 127-135 (2014) Table |. Collection details for this study. Code CM JAMO1 50 YPT JAMO2 50 YPT JAMo3 sweep 11:00-13:00 JAMo4 sweep 15:00-17:00 JAM05 sweep 11:00-12:00 JAMO06 | 1 | St. Andrew, Hollywell Park| 18.08609, -076.72629 sweep 15:30—16:00 JAM07 St. Mary, Oracabessa _| 18.40207, -076.92519 SUV EA JAMO8 | 2 St. Mary, Oracabessa | 18.40324, -076.92727 15-17.xi.2010 50 YPT JAMO09 | 2 St. Mary, Oracabessa _| 18.40260, -076.92519 16.xi.2010 | sweep 10:00—11:00 JAM10 | 3 Trelawny, Windsor 18.35752, -077.65837 18.xi.2010 | sweep 16:00-17:00 JAM11 | 3 Trelawny, Windsor 18.35752, -077.66406 19-21.xi.2010 50 YET. JAM12 | 3 Trelawny, Windsor 18.35823, -077.05675 19-21.xi.2010 50 YPT JAM13 | 3 Trelawny, Windsor 18.35169, -077.66371 19.xi.2010 | sweep 14:30-15:30 JAM 14 | 3 Trelawny, Windsor 18.35531, -077.66371 20.xi.2010 | sweep 11:00—12:00 JAM15 | 3 Trelawny, Windsor 18.35838, -077.65837 20.xi.2010 | sweep 15:00—15:30 JAM16 | 3 Trelawny, Windsor 18.35838, -077.65837 21.xi.2010 | sweep 15:00—16:30 Code= collecting event, L= locality, Place includes Jamaican parish and town, Alt.= altitude in metres within 5 metres, CM= collecting method (YPT= yellow pan traps, sweep= sweep netting, plus the time of day during which sweep netting was carried out). JAMO03-05 were carried out in the vicinity of fast-flowing mountain streams, with the soil inside the forest patches rich in organic matter. In addition, during collecting events JAM01 to 05 it was sunny, while during event JAMO06 there was fog, complicating the sweep netting. Locality 2 consisted of an approximate area of 0.0066 km? (1.63 acres), at altitudes between 167 and 176 m.a.s.l., with collecting carried out mostly inside woodlands with moderate canopy cover on limestone ground. There was no evident water body in the vicinity. The main disturbing factor during collecting events JAM07 and JAM08 was the heavy rain, which flooded the yellow pan traps left out during the night. Locality 3 consisted of an approximately 0.29 km? (70.64 acre) area, at altitudes between 82 and 173 m.a.s.l., within Jamaica’s Cockpit Country, an area containing one of the islands’ last contiguous rainforests, although collecting events JAM10-12 and JAM15 took place on the edge of the forest. The only registered water body within the locality was a spring near collecting event JAM15, a tributary to the Martha Brae river. No noteworthy climatic events affected the collecting events JAM10-16. All parasitoid wasps collected were stored in 96% EtOH and subsequently identi- fied in the laboratory using a dissecting microscope. Identifications were made at least to family level and in some cases to genus. However, due to the lack of expertise for most families and due to time constraints, we are at this moment unable to present data at species (or even genus) level for all families, so in the absence of an equal taxo- nomic treatment of all families, we present the data at family level. The total number of wasp families was recorded for each locality, and calculations were made adjusting the number of wasp families collected for each site to obtain a unit measurement for Parasitoid wasps from three Jamaican localities: A pilot study 131 collecting effort. For the yellow pan traps the number of wasp families was divided by the number of hours the YPT's were left out, and for the sweep net collection, the number of families was divided by the number of people multiplied by the number of hours spent collecting. All parasitoid wasps collected during this study were deposited at the Coleccién Nacional de Insectos, Instituto de Biologia, Universidad Nacional Auténoma de México, with accession numbers CNIN-JAM0001-1522. Results In this pilot study, we collected a total of 1522 individual parasitoid wasps in the three localities belonging to 15 families and one superfamily (for more details see Table 2 and Suppl. metrial 1). To under- rather than overestimate the number of families, we will count the superfamily, Cynipoidea, as one additional family, making the total number of families collected in this study at least 16. The highest proportion of parasitoid wasps collected in locality 1 belong to the family Diapriidae (especially during the collecting events JAMO1 and 02 where we used yellow pan traps), in locality 2 to the family Ich- neumonidae and in locality 3 to the Pteromalidae. In total, specimens belonging to 13, 10 and 13 parasitoid wasp families were collected in localities 1, 2 and 3, respectively. Specimens belonging to the families Braconidae, Chalcididae, Cynipoidea (superfam- ily), Diapriidae, Eulophidae, Ichneumonidae, Platygastridae and Pteromalidae were found in all three localities. Additionally, specimens belonging to the family Mymaridae were only found in localities 1 and 2, specimens belonging to the families Bethylidae and Ceraphronidae were only found in localities 1 and 3, specimens belonging to the family Encyrtidae were only found in localities 2 and 3, specimens belonging to the families Megaspilidae and Proctotrupidae were only found in locality 1 and specimens belonging to the families Agaonidae and Eupelmidae were only found in locality 3. When accounting for collecting effort, the yellow pan traps were most efficient in locality 1 at family level, meaning that in this locality, using YPTs as a collecting method yielded individuals form more families than in the other two localities. On the other hand, sweep netting was most efficient in locality 3 per unit time (see Figure 2). Parasitoid wasps from most families were collected both in YPT's and sweep nets. The minor differences consisted in the single individuals belonging to the families Agao- nidae and Eupelmidae collected by sweep netting but not in YPTs, and the single megaspilid collected by YPT only. Also, in terms of individuals, a higher number of ceraphronids, diapriids, mymarids and platygastrids was collected using YPTs, while for the remaining families more individuals were collected by sweep netting than using YPTs (see Table 3). However, this should not be taken as hard evidence for preferring one method over the other for several reasons. First of all, presenting data in terms of individuals does not equate to species richness; second, collecting effort was not stand- ardised; and thirdly, the numbers we are dealing with in this study are generally low. For these reasons no tests of significance were carried out with regards to differences in productivity between sampling methods. 132 Fadia S. Ceccarelli et al. / Journal of Hymenoptera Research 37: 127-135 (2014) Table 2. Number of individual wasps collected from each locality for all families. Famil Agaonidae Bethylidae Braconidae TOTAL a eal Ceraphronidae Chalcididae Cynipoidea (unidentified families) Diapriidae Encyrtidae Eulophidae Eupelmidae Ichneumonidae Megaspilidae Mymaridae Platygastridae Proctotrupidae Pteromalidae TOTAL INDIVIDUALS Number of families Figure 2. Efficiency of collecting methods. Pie charts representing the efficiency of the two collecting methods used in this study at family level (YPT= yellow pan traps; sweep = sweep net) in units (calculated as described in the Materials and Methods section) for each locality (black= locality 1, grey= locality 2, white= locality 3). Discussion The differences between the three localities with regards to the parasitoid wasp families sampled in this study could be attributed to a combination of topology, climate and collecting method. For example, in locality 1 relatively few families were represented in Parasitoid wasps from three Jamaican localities: A pilot study 133 Table 3. Number of individual wasps collected by the two collecting methods for all families. Family Yellow pan traps sweep netting Agaonidae 0 1 Bethylidae 1 3 Braconidae 148 153 Ceraphronidae 4 3 Chalcididae 1 6 Cynipoidea (unidentified families) 30 a9, Diapriidae 295 84 Encyrtidae 2 2, Eulophidae pe 26 Eupelmidae 0 1 Ichneumonidae 22 50 Megaspilidae 1 0 Mymaridae 23 2, Platygastridae 168 58 Proctotrupidae 7 6 Pteromalidae 151 153 TOTAL INDIVIDUALS 875 647 Number of families 14 15 sweep net collections compared to the other two localities. The reasons for this may be that walking the steep slopes and rugged terrain by mountain streams hindered maxi- mum collecting efficiency with a sweep net while the thick fog during collecting event JAM06 definitely lowered the average for the families collected in locality 1. Similarly, the yellow pan traps appeared to be the least efficient in locality 2, however, the heavy rains washing out most of the specimens collected in the traps definitely skewed the results in favour of localities 1 and 3 for YPTs. ‘The fact that the YPTs were most ef- ficient in locality 1 with a high proportion of Diapriidae collected in this locality sup- ports the fact that Diapriidae are efficiently collected using YPTs (e.g. Noyes 1989) in areas rich in organic matter (Masner and Gracia 2002). As mentioned before, the two collecting methods used in this study are not comparable as to efficiency. However, as in previous studies (e.g. Noyes 1989, Missa et al. 2009), we show that increasing the number of collecting methods may increase the chances of collecting parasitoid wasps from different families, even though according to Missa et al. (2009) habitat type is a more important factor than collecting method in determining the parasitoid wasp species collected. Given more time and more sampling methods than used in this study, differenc- es in parasitoid wasp family assemblages between localities are more likely to display structuring based on host species assemblages, in turn driven by differences in plant assemblages. Sampling during different seasons throughout the year is also likely to yield different assemblages to those found in this study. Nevertheless, the high numbers of parasitoid wasps belonging to a considerable number of families collected during a 134 Fadia S. Ceccarelli et al. / Journal of Hymenoptera Research 37: 127-135 (2014) relatively short time using only two basic collecting techniques provide evidence that Jamaica is definitely a place worth sampling for future studies on or including these taxa. In addition to collecting for general ecological studies, hymenopterists wishing to undertake studies on specific families may also be able to verify in this pilot study the most appropriate locality for collecting the specific taxon which they wish to investigate. Acknowledgements We thank all the people who facilitated our field work while in Jamaica, especially Oliver Magnus and Time Anson. We also extend our gratitude to Juan José Martinez and Juliano Nunes who helped during the process of wasp identification, and two anonymous referees for comments on a previous version of this manuscript. This work was supported by and a grant given by CONACYyT (convocatoria SEP Ciencia Basica 2008) to AZR. References Abrahamczyk S, Steudel B, Kessler M (2010) Sampling Hymenoptera along a precipitation gradient in tropical forests: the effectiveness of different coloured pan traps. Entomologia Experimentalis et Applicata 137: 262—268. doi: 10.1111/j.1570-7458.2010.01063.x Alam MM (1990) Diamondback moth and its natural enemies in Jamaica and some other Carib- bean Islands. In: Talekar NS (Ed) Diamondback moth and other crucifer pests: Proceedings of the Second International Workshop. Asian Vegetable Research and Development Center, Shanshua (Taiwan), December 1990: 233-243. Burke K (1988) Tectonic evolution of the Caribbean. Annual Review of Earth and Planetary Sciences 16: 201—230. doi: 10.1146/annurev.ea.16.050188.001221 Dolphin K, Quicke DLJ (2001) Estimating the global species richness of an incompletely de- scribed taxon: an example using parasitoid wasps (Hymenoptera: Braconidae). Biological Journal of the Linnean Society 73 (3): 279-286. doi: 10.1111/j.1095-8312.2001.tb01363.x Egeleton P, Belshaw R (1992) Insect parasitoids: an evolutionary overview. Philosophical Transactions of the Royal Society London B 337: 1-20. doi: 10.1098/rstb.1992.0079 Jones OR, Purvis A, Baumgart E, Quicke DLJ (2009) Using taxonomic revision data to esti- mate the geographic and taxonomic distribution of undescribed species richness in the Bra- conidae (Hymenoptera: Ichneumonoidea). Insect Conservation and Diversity 2: 204—212. doi: 10.1111/j.1752-4598.2009.00057.x LaSalle J, Gauld ID (1991) Parasitic Hymenoptera and the biodiversity crisis. Redia 74: 315-334. Lewis CN, Whitfield JB (1999) Braconid wasp (Hymenoptera: Braconidae) diversity in forest plots under different silvicultural methods. Environmental Entomology 28: 986-997. Losos JB, Schluter D (2000) Analysis of an evolutionary species—area relationship. Nature 408: 847-850. doi: 10.1038/35048558 Parasitoid wasps from three Jamaican localities: A pilot study 135 Martinez JJ, Ceccarelli FS, Zaldivar-Riverén A (2012) Two new species of Pambolus (Hyme- noptera, Braconidae) from Jamaica. Journal of Hymenoptera Research 24: 85-93. doi: 10.3897/JHR.24.2300 Masner L, Garcia RJL (2002) The genera of Diapriinae (Hymenoptera: Diapriidae) in the New World. Bulletin of the American Museum of Natural History 268: 1-138. doi: 10.1206/0003-0090(2002)268<0001:TGODHD3>2.0.CO;2 Missa O, Basset Y, Alonso A, Miller SE, Curletti G, De Meyer M, Eardley C, Mansell MW, Wagner T (2009) Monitoring arthropods in a tropical landscape: relative effects of sam- pling methods and habitat types on trap catches. Journal of Insect Conservation 13 (1): 103-118. doi: 10.1007/s10841-007-9130-5 Noyes JS (1989) A study of five methods of sampling Hymenoptera (Insecta) in a tropical rainforest, with special reference to the Parasitica. Journal of Natural History 23: 285-298. doi: 10.1080/00222938900770181 Ord TJ, Stamps JA, Losos JB (2013) Convergent evolution in the territorial communication of a classic adaptive radiation: Caribbean Anolis lizards. Animal Behaviour 85: 1415-1426. doi: 10.1016/j.anbehav.2013.03.037 Quicke DLJ (1997) Parasitic Wasps. Chapman & Hall, London: 1-492. van Benthem S, Govers R, Spakman W, Wortel R (2013) Tectonic evolution and mantle structure of the Caribbean. Journal of Geophysical Research: Solid Earth 118: 3019-3036. doi: 10.1002/jgrb.50235 Supplementary material | Collection data Authors: Fadia S. Ceccarelli, Dwight E. Robinson, Hans Clebsch, Alejandro Zaldivar- Riveron Data type: Collection details Explanation note: Table showing the number of individual parasitoid wasps collected during this study in each collecting event. Copyright notice: This dataset is made available under the Open Database License (http://opendatacommons.org/licenses/odbl/1.0/). The Open Database License (ODDbL) is a license agreement intended to allow users to freely share, modify, and use this Dataset while maintaining this same freedom for others, provided that the original source and author(s) are credited. Link: doi: 10.3897/JHR.37.7081.app1