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Heredity 72 (1994) 228—236 Received 7 July 1993 Genetical Society of Great Britain

Population structure of a predatory : the importance of for intertrophic level interactions

MOSHE COLL*, LAURA GARCIA DE MENDOZA & GEORGE K. RODERICKt Department of , University of Maryland, College Park, MD 20742, U.S.A.

Migrationand gene flow of natural enemies play an important role in the stability of predator—prey interactions and organization in both natural and managed systems. Yet, relative to that of their herbivorous prey, the genetic structure of natural enemy has been little studied. We present evidence that populations of the predatory coccinellid beetle maculata (Coleoptera: ), are not genetically subdivided and that levels of gene flow among these populations are extremely high. Furthermore, in the same geographical area, gene flow of C. maculata was significantly (one of magnitude) greater than that of an abundant prey , the Colorado beetle decemlineata (Coleoptera: Chrysomelidae). The high mobility of this natural enemy relative to the insect on which it feeds may contribute to its effectiveness as a biological control agent in agricultural systems.

Keywords:allozyme,biological control, electrophoresis, gene flow, , natural enemies.

Introduction Despite the recognized importance of mobility of natural enemies, little is known about their Thegenetic structure of populations is a of structure, especially the amount of gene flow their spatial arrangement and amount of gene flow (Roderick, 1992) and dispersal (CoIl, 1991) among among them. The extent of gene flow will determine field populations. This lack of information stands in not only the potential for populations to diverge gene- contrast to the studies of the genetic structure of herbi- tically but will also influence local population vorous insect populations in both natural (Slatkin, dynamics. For predatory species, these effects are also 1985a, 1987; McCauley & Eanes, 1987) and managed likely to be coupled with the dynamics and movement systems (Loxdale & den Hollander, 1989; Roderick & of their prey. The association between predator and Caldwell, 1992). prey is well illustrated, theoretically and experi- Many studies have examined the role gene flow mentally, by predators and (collectively plays in the development of local in herbi- termed natural enemies) and the herbivorous vores, including the of host races (Butlin, which they attack. For example, movement of natural 1990; Roderick, 1993) and the development of insecti- enemies may contribute to their aggregative response cide in species (Comins, 1977; to sites harbouring varying numbers of prey (Murdoch Georghiou & Taylor, 1977; Taylor & Georghiou, et aL, 1985; Strong, 1988). Under some conditions, 1979; Tabashnik & Croft, 1982; Caprio & Tabashnik, such aggregative response by natural enemies may 1 992b). Selection pressure from application have, at least theoretically, stabilizing effects on popu- will also affect natural enemies (Rosenheim & Hoy, lations (Hassell, 1978; Hassell & May, 1988) or meta- 1986; Rosenheim & Tabashnik, 1991). In general, low populations (Taylor, 1991) of predators and prey. levels of gene flow may permit local such as the evolution of resistance (Caprio & Tabaslmik, 1 992b). If natural enemies are indeed more mobile than their hosts or prey (Murdoch et a!., 1985) *Correspondence. USDA, ARS, Insect Biocontrol Laboratory, then natural enemies may not develop insecticide BARC-East, Bldg. 402, Beltsville, MD 20705, U.S.A. resistance as rapidly as their herbivorous prey. In turn, tPresent address: Hawaiian Evolutionary Program, University of , 3050 Maile Way Gilmore 310, Honolulu, HI differences in susceptibility to between 96822, U.S.A. herbivores and natural enemies may facilitate pest out- 228 GENE FLOW IN A PREDATORY BEETLE 229 breaks and resurgence because of the removal of predators and parasites by pesticide applications. It is Methods unclear, however, how differences in gene flow between natural enemies and their herbivorous prey affect their susceptibility to insecticides. Biological material Two approaches are commonly used to estimate Thepredatory beetle C.maculatais native to North gene flow among populations: direct measures, such as America and is widely distributed east of the Rocky release—recapture, and indirect estimates based on pat- Mountains (Obrycki & Tauber, 1978). In both natural terns of genetic similarity among populations (Slatkin, and managed systems, larvae and adults are important 1985a, 1987). Although direct measures of dispersal natural enemies of , insect and soft-bodied represent actual observations, they may be biased by immatures (Smith, 1960; Atallah & Newsom, 1966; not reflecting rare gene flow events or non-random Warren & Tadic, 1967, and references therein). The contributions to subsequent generations (Ehrlich & predator is common in maize, , , potato, Raven, 1969; Endler, 1979; Slatkin, 1987). By tobacco, curcubits and cole crop systems (Ewert & contrast, indirect estimates of gene flow, based on FST Chiang, 1966; Richardson & DeLoach, 1973; Elsey, (Wright, 1951) or rare alleles (Slatkin & Barton, 1989), 1974; Wright & Laing, 1980; Marck & Smilowitz, reflect variations in allele distribution that were pro- 1982; Cosper etal., 1983; Groden etal., 1990; Coll & duced over long periods (Slatkin, 1987; McCauley, Bottrell, 1991; Hazzard et al., 1991). In potatoes, C. 1991). maculata can be a major natural enemy of the In this study, we first used allozyme electrophoresis (Groden et al., 1990; Hazzard to examine the population structure of a predatory & Ferro, 1991; Hazzard et at., 1991). beetle, De Geer (Coleoptera: Six populations of overwintering adult C. maculata Coccinellidae). Then, we tested the hypothesis that were sampled in Maryland, U.S.A., between 31 March level of gene flow among populations of this predator is and 10 April 1992 (Fig. 1). The sampling sites were in greater than that among populations of one of its sym- the following counties: Washington (39°30'55"N; patric abundant prey species, the Colorado potato 77°44'50"W), Frederick (39°16'05"N; 77°28'05"W), beetle, Leptinotarsa decemlineata Say (Coleoptera: Montgomery (39°1 7 '30 "N; 77°1 2'25 "W), Howard Chrysomelidae). (39°12'45"N; 76°56'lO"W), Prince George

I I I 0 25 50 75 100 1cm Fig. ICollectionsites of six Coleomegilla maculata overwintering aggregations in Maryland, U.S.A. 230 M.COLLETAL.

(39°00'40"N; 76°49'55"W) and Anne Arrundel these systems were adopted from Hebert & (38°55 '50 "N; 76°3 7 '45 "W). The approximate distance Beaton (1989). Electromorphs were labelled alpha- between the westernmost and the easternmost popula- betically with 'A' as the fastest running electromorph. tions was 116 km. The were collected from overwintering aggregations at the base of prominent Genetic trees at the edge of maize fields. Since C. maculata analysis does not exhibit a long distance migratory behaviour to Thefixation index, FST is a measure of genetic dif- overwintering sites (Hagen, 1962), all beetles collected ferentiation among populations and can range between from the same aggregation are considered to belong to 0 (no genetic differentiation) and 1 (complete dif- the same population or random breeding unit. The ferentiation) (Wright, 1951). It has several equivalent beetles were maintained in the laboratory (25 3°C interpretations. FST can be expressed as the absence of 15:9 L : D) until they were no longer in heterozygotes in subpopulations relative to what is (determined by flight and feeding behaviours) and after expected in the total population (i.e. FST= (HT HS)/HT, any parasitoids (Dinocampus (=Perilitus)coccinellae where H is the average heterozygosity of subpopul- (: )) had emerged (about 25 ations and HT is the predicted total heterozygosity). FST April). The beetles were frozen at —80°Cuntil pre- also represents the standardized variance in allele fre- paration for electrophoresis. quencies among local populations (Weir, 1990). While these formulations of FST are for one locus and one allele, similar statistics can be estimated for two alleles Electrophoresis at one locus (Wright, 1951) and for more alleles at Cellulose-acetategels (Helena Laboratories Inc.) were many loci (as GST; Nei, 1973, 1977; Birky eta!., 1989). used for electrophoresis (Richardson et al., 1986; An alternative to FST is the statistic of coancestry, 0, Hebert & Beaton, 1989). Before electrophoresis, which represents the correlation of genes of different beetles were homogenized individually in 50 4u1 of dis- individuals in the same populations (Weir & Cocker- tilled water and centrifuged for 5 mm at 4°C. Resolving ham, 1984; Weir, 1990). gels were maintained at 4°C during electrophoresis. A For neutral alleles, FST, GST or 0, can be used to preliminary survey of 17 enzyme systems revealed nine estimate the number of migrants exchanged by popula- polymorphic resolvable loci. The following seven tions per generation (gene flow) (FST =1/(4Nem+ 1), enzyme systems encoded by nine presumptive loci where Ne is the effective local and m is were scored in all six populations: fumarate hydratase the average rate of immigration or the proportion of (FUM); isocitrate dehydrogenase (IDH, two loci: fast the population that migrate each generation (Wright, andslow [s]);malatedehydrogenase (MDH, two loci: 1943)). By estimating Nem we can compare the magni- [fands]); peptidase (PEP); 6-phosphogluconate tude of gene flow without the need for exact estimates dehydrogenase (6PGDH); phosphoglucose isomerase of the average effective population size, Ne. (PGI) and phosphoglucomutase (PGM). The buffer Wright's formula assumes an 'island model' in which systems found to be most suitable for resolving the every local population is equally likely to exchange above loci are listed in Table 1. Staining techniques for migrants with any other. However, the formula also

Table 1 Presumptive loci scored for Coleomegilla maculata

Enzyme E.C. Locust Buffert

Fumarate hydratase 4.2.1.2 FUM Tris-EDTA-Borate 0.13 M, pH 8.9 Isocitrate dehydrogenase 1.1.1.42 IDH-f Citrate Phosphate 0.01 M, pH 6.4 IDH-s Citrate Phosphate 0.01 M, pH 6.4 Malate dehydrogenase 1.1.1.37 MDH-f Tris-Maleate-EDTA-MgC12 0.05 M, pH 7.8 MDH-s Tris-Citrate 0.1 M, pH 8.2 Peptidase 3.4.11-13 PEP Tris-Glycine 0.025 M,pH 8.5 6-Phosphogluconate deliydrogenase 1.1.1.44 6PGDH Tris-Maleate-EDTA-MgCI2 0.05 M, pH 7.8 Phosphoglucose isomerase 5.3.1.9 PGI Citrate Phosphate 0.01 M, pH 6.4 Phosphoglucomutase 2.7.5.1 PGM Tris-Glycine 0.025 M, pH 8.5 and Tris-Maleate-EDTA-MgCl2 0.05 M, pH 7.8 tf°= fast and s =slowelectromorphs. IHebert & Beaton (1989). GENE FLOW IN A PREDATORY BEETLE 231 approximates gene flow for two-dimensional stepping- We used BIOSYS-1 (FORTRAN 77 version, Swofford stone models (Crow & Aoki, 1984; Crow, 1986; & Selander, 1981) to analyse gene frequency data. For Slatkin, 1987). Indirect methods to estimate gene flow each locus, as well as over all loci, we estimated GST rely on several rarely evaluated assumptions. Four and 0 as well as F1, which measures deviation from major assumptions must be made (Daly, 1989). (i) random mating within subpopulations. We scored Gene flow is random with respect to the 6—11 alleles per locus and could not completely studied. (ii) The rate of gene flow for the studied alleles resolve one allele (PEP, allele G; Appendix A). exceeds the rate of change of allele frequencies due to To test the assumption of Wright's (1951) island selection. (iii) The rate of gene flow exceeds a minimum model (i.e. that a migrant from a population is equally level to offset the effects of . (iv) The popu- likely to move to any other population), we correlated a lations are at genetic equilibrium, such that a balance is measure of genetic distance between pairs of popula- achieved between loss of alleles by drift and the gain of tions (Roger's Modified Distance; Wright, 1978) alleles from migration. These assumptions are con- against the geographical distance between these popu- sidered in turn below. lations. We used a resampling procedure (Mantel's test; The first two assumptions are likely to be met for Mantel, 1967; Crowley, 1992) to correct for lack of allozymes that are considered to be either neutral or independency between data points. under weak selection (Kimura, 1983). Also, if many Finally, we tested whether the 0 estimate (unbiased loci give similar results, it would be difficult to argue regardless of sample size: Chakraborty & Leimar, that all are responding to the same selective pressures 1987) for C. maculata is lower than that for L. decem- (Slatkin, 1987). The last two assumptions are more dif- lineata (G. K. Roderick et a!. and M. L. Azeredo-Espin ficult. For the third assumption, Wright (1931) showed et a!., both unpublished data). Both sets of estimates that any gene flow among populations will prevent were obtained over the same geographical area in complete fixation and that genetic drift will only lead to Maryland. We used nine loci for C. maculata and six substantial genetic differentiation if gene flow does not for L. decemlineata. Because sampling distributions of exceed a certain minimum level. This condition can be gene diversity components are not known, we used the expressed as m>> 1/(4N)or Nem>> 1/4 (Wright, 1931). Mann—Whitney U-test (SAS Institute, 1985) to com- Free-living, mobile usually have much higher pare the two estimates of 0. levels of gene flow. The fourth assumption states that the populations are in genetic equilibrium, such that Results loss of alleles by genetic drift in any population is balanced by a gain in alleles through migration. At Electromorphfrequency data are presented in Appen- equilibrium this balance will hold over a range of popu- dix A. Data indicate that C. maculata has an extremely lation sizes (Slatkin, 1987). Because C. maculata is high number of alleles per locus (9.44 0.73). Simi- native to , we argue that there has been larly, Steiner & Grasela (1993) found twice as many sufficient time for the effects of migration to balance alleles per locus in C. maculata than in other beetle the effects of genetic drift. species. In our study, allozyme frequencies did not Slatkin & Barton (1989) suggested that estimation of deviate significantly from Hardy—Weinberg expecta- gene flow based on FST methods (including GST and 0) tions (x2goodness-of-fittest with a Sidak adjusted P is preferable to other methods that use allele frequency value; Sokal & Rohlf, 1981). Thus, within the six data (such as, the private alleles and maximum likeli- studied populations, there is no evidence of significant hood methods; Slatkin & Barton, 1989). The use of deviations from random mating for any of the loci (also rare or private alleles (Slatkin, 1985b) is more sensitive suggested by the relatively low F1 value; Table 3). to coding errors than methods based on FST and maxi- Contingency chi-square analysis revealed that there mum likelihood methods appear to overestimate gene were no significant differences in allele frequencies at flow unless a large number of populations (perhaps as each locus across populations (x2= 80.67,d.f. =75, many as 40) is sampled (Slatkin & Barton, 1989). For 0.1

Colorado potato beetle eggs and young larvae (Groden mated at approximately 100,000 adults. Because the et al., 1990; Hazzard & Ferro, 1991; Hazzard et aL, effective population size may be smaller by as much as 1991). Over the same geographical area, estimates of 90 per cent (Wright, 1978), an upper limit of the aver- genetic differentiation for the Colorado potato beetle age migration rate, m, is 0.02 (Nem =166.4; were significantly greater than for C. maculata and Ne= 10,000). Gene flow at this level is too low therefore the estimated level of migration was signifi- to retard significantly the development of resistance in C. cantly lower than that for C. maculata. maculata by high immigration of susceptible beetles Greater levels of population differentiation, relative from untreated fields and yet is too high to slow the to C. maculata, were also evidenced in other prey spread of initially rare, resistant alleles (Caprio & species. For several North American lepidopteran Tabashnik, 1 992a, b). pests fed on by C. maculata, FST ranged from 0.02 1 to The mobility of predators and parasites in both 0.084 (Pashley et al., 1985) and for surface-dwelling natural and managed systems is clearly important in coleopteran prey (excluding predatory and cave- determining the stability of predator—prey interactions dwelling species) FST values ranged from 0.011 to and in insect . Yet, few previous studies 0.154 (McCauley & Eanes, 1987; Hsiao, 1989). By have examined the population structures of both contrast, small genetic differentiation of C. maculata, predator and prey in the same system (Taylor, 1991). suggests that its movement may be one or even two Such studies are likely to be rewarding not only for orders of magnitude greater than that of its prey. This what they will reveal about the organisms themselves difference in mobilities may help to explain the but also for what they will contribute to our under- remarkable efficiency of C. maculata, even in the face standing of and community of a yearly destruction as found in annual organization. cropping systems. Differential mobility of predators and their prey is also likely to be important in the evolution of pesticide Acknowledgements resistance. Often, pest species are more resistant to Wethank C. Smith for assistance, C. Mitter and M. M. than natural enemies (Croft & Brown, 1975; Yang for advice and R. Gillespie, A. Hilbeck, M. Tabaslmik, 1986). Two hypotheses have been Johnson and an anonymous reviewer for helpful com- advanced to explain this phenomenon; preadaptation ments on drafts of the manuscript. This work was (Gordon, 1961) and food limitation (Huffaker, 1971; funded by grants from the USDA (to G.K.R.), the Georghiou, 1972). Our results suggest yet another Maryland Agricultural Experiment Station Competi- mechanism: the higher mobility of natural enemies tive Grants Program (to G.K.R. and M.C.), the General relative to their prey may slow the evolution of pesti- Research Board of the University of Maryland (to cide resistance: (1) because natural enemies may move G.K.R.), and NIH Biomedical Research Funds (to more readily out of treated areas (in response to prey G.K.R.). The Department of Entomology, University of scarcity) and thus be less exposed to pesticide selection Maryland and the Hawaiian Pro- pressure and/or (2) because more susceptible in- gram, University of Hawaii, provided additional sup- dividuals may immigrate into treated fields to dilute the port. This is scientific article A6414, contribution selective effect of pesticides. 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Appendix A Electromorph frequencies and sample size (N)forsix popu- lations of Coleotnegi/la macu/ala. See Table 1 and Fig. I for Population abbreviations of loci and populations, respectively Locus Allele KEED R-28 DAM R-108 BELT R-424

Population Locus Allele KEED R-28 DAM R-108 BELT R-424 D 0.9890.9780.9780.9460.9860.978 E 0.0000.0220.0000.0110.0000.011 FUM (N) 45 45 46 46 35 45 F 0.0000.000(3.0110.0110.0140.011 A 0.0000.000 0.0110.0000.0000.000 J'EP (N) 45 44 46 46 34 44 B 0.0000.011 0.0000.0000.0000.000 A 0.000 0.0000.0110.0330.0000.023 C 0.0000.011 0.0000.0000.0000.000 B 0.0560.0570.0980.0650.0590.045 D (3.0000.000 0.0000.0110.0000.000 C 0.000(3.0570.0000.0110.0150.034 E 0.0110.011 0.0000.011(3.0000.0 11 D 0.2780.2050.3040.2070.2940.250 F 0.9560.944 0.9670.9460.9710.944 E 0.0110.0000.0000.0000.0290.000 G 0.0110.000 0.0110.0110.0000.000 F 0.5330.6250.4670.5870.5590.580 H 0.0000.000 0.0000.0000.0140.011 G' 0.1000.0230.1090.0870.0440.068 1 0.0000.000 0.0000.01 10.0000.011 H 0.0110.0110.0000.0000.0000.000 J 0.0110.000 0.0000.0000.0000.000 1 0.0110.0000.0110.0000.0000.000 K 0.011 0.022 0.0000.0000.0140.011 J 0.0000.0000.0000.0110.0000.000 L 0.0000.000 0.0110.011 0.0000.000 K 0.0000.0230.0000.0000.0000.000 M 0.0000.000 0.0000.0000.0000.011 6PGDH(N) 43 44 46 46 35 45 45 44 46 46 35 45 IDH-f (N) A 0.000 0.0230.0110.0000.0000.000 A 0.0000.000 0.0000.0000.0140.000 B 0.0000.0000.0110.0110.0000.000 B 0.0110.000 0.0000.0000.0000.000 C 0.0000.0000.0000.0220.0000.011 C 0.0110.000 0.0110.0000.0000.000 D 0.0000.0230.0220.0000.0000.011 D 0.0000.023 0.0330.0000.0140.000 E 0.0000.0000.0000.0000.0140.000 E 0.0000.000 0.0000.0000.0140.000 F 0.9650.9090.9130.9240.9430.956 F 0.9670.909 0.9460.9570.8860.978 G 0.0230.0110.0110.0110.0140.000 G 0.0110.034 0.0110.0430.0290.022 H 0.0120.0340.0330.0330.0290.022 H 0.0000.011 0.0000.0000.0000.000 I 0.0000.000 0.0000.0000.0140.000 PGI (N) 45 44 44 46 35 44 J 0.0000.023 0.000(3.0000.0000.00(3 A 0.000 0.0110.0230.0110.0000.000 K 0.0000.000 0.0000.0000.0290.000 B (3.0220.0000.0110.0000.0140.011 C 0.111 (3.1360.2160.1850.1430.205 IDH-s (N) 45 43 46 46 35 46 D 0.6890.5800.4770.554 A 0.0000.012 0.0220.0000.0000.000 0.6430.557 E 0.0000.0230.0000.0330.0000.023 B 0.0000.000 0.0000.0000.0000.022 F 0.1220.1590.1700.0870.114 C 0.0110.012 0.0000.0000.0000.000 0.170 G 0.0220.0000.0000.0540.0000.000 D 0.0000.012 0.0110.0110.0140.033 H 0.0330.0910.0680.0650.0710.023 E 0.9560.953 0.9350.9670.9860.913 1 0.0000.0000.01 10.0000.0 140.011 F 0.0000.01 2 0.0000.0000.000(3.000 J 0.0000.0000.0230.0 110.0000.000 G 0.0220.000 0.0220.0000.0000.000 H 0.0000.000 0.0000.0110.0000.011 PGM (N) 45 39 44 46 34 45 1 0.0110.000 0.0000.0110.0000.022 A 0.000 0.0000.0000.0000.0150.000 J 0.0000.000 0.0110.0000.0000.000 B 0.011 0.0 130.0000.0110.0440.000 C 0.0670.0510.0340.0330.0590.044 45 45 46 46 35 46 MDH-f (N) D 0.3220.3590.3980.4240.4410.367 A 0.0000.000 0.0000.0000.0140.000 E 0.0000.0000.0000.0220.0000.011 B 0.0000.000 0.0000.0110.0140.000 F 0.5670.5380.4320.4350.4120.533 C 0.0000.000 0.0000.0110.0 140.000 G 0.0000.0260.0570.0000.0000.000 D 0.9781.000 0.9780.9350.9570.978 H 0.0330.0130.0680.0760.0290.044 E 0.0000.000 0.0000.0220.0000.022 1 0.0000.0000.0110.0000.0000.000 F (3.0220.000 0.0110.0220.0000.000 G 0.0000.000 0.0110.000 0.000 0.000 'Allele could not he completely resolved. It consists of MDH-s (N) 45 45 46 46 35 45 several electromorphs with a continuous range of mobilities. A 0.0110.000 0.0000.0110.0000.000 B 0.0000.000 0.0110.0110.0000.000