Open Access
How to translate text using browser tools
1 March 2014 Alpha and Beta Diversity of Lepidoptera in Eucalyptus Plantations in the Amazonian Region of Brazil
José Cola Zanuncio, Pedro Guilherme Lemes, Germi Porto Santos, Carlos Frederico Wilcken, Bruno Zaché, Rosenilson Pinto, José Eduardo Serrão
Author Affiliations +

The Lepidoptera are among the insect groups with the greatest species diversity and ecological services. The distribution, abundance and variation in time and space of species in natural communities are important. The occurrence of pests (primary pest species) and those species with potential to cause damage (secondary pest species), plus other species, are studied in monitoring programs in forest plantations as groups I, II and III, respectively. The objective of this work was to study alpha and beta diversity patterns, and the effect of native forest in these indexes by monitoring Lepidoptera in eucalyptus plantations in the Amazonian region of Brazil. Surveys were conducted with light traps at 4 sites in this region. Alpha diversity was calculated with the Jackknife first-order procedure and beta diversity with the Jaccard index in order to estimate the dissimilarity per point and the effect of the distance between the native forest and the plantations on the Lepidoptera fauna. The richness showed 10 or 11 species of group I; 9 or 10 species of II and 378 to 409 species of III, without differences per group between regions. The curves of accumulated number of primary pest species stabilized between the 15th and 35th samplings and those for secondary pest species stabilized in the range from 20th to 70th samplings, with variations among sites. The estimation of richness for species of group III ranged from 50 to 100 species with a steep slope of the curve until approximately the 60th sampling with a slow increase and a tendency of stabilization in the 4 areas after this date. The primary pest species were the same in all areas and therefore their beta diversity was zero. The dissimilarity of secondary pests was similar between areas except for Felipe. Group III showed lower dissimilarity between Caracuru and Ponte Maria (14.88%) and highest values between Felipe and Pacanari (21.64%). The lower number of individuals of group I in Felipe and Ponte Maria and lower species richness of group III in Felipe can be explained by the proximity of eucalyptus plantations to the native forest. The knowledge of population dynamics and species richness of Lepidoptera defoliators is important for pest management. These indexes allow a better detection of species with a history of damage and decision-making with the most appropriate preventive measures for each situation.

Insects have important role in the ecosystems as herbivores, pollinators, nutrient cyclers, regulating populations of other organisms and feeding on or serving as food for other species (Losey & Vaugan 2006; Losey & Vaugan 2008; Lemos et al. 2003). The Lepidoptera are among the largest groups of insects with great diversity and different ecological services (Summerville & Crist 2008; Pereira et al. 2008). However, climate change can reduce the number and diversity of Lepidoptera (Gimesi et al. 2012).

The insect species richness in tropical rainforest ecosystems is high and its evenness is low, with a few abundant ones and mostly rare species (Hill & Hamer 1998; Nummelin 1998). Tropical rainforests have more species than temperate habitats, but their abundance and distribution in these communities need to be better studied (DeVries et al. 2009). Local and regional species richness may improve understanding of the relative influence of regional and local processes on community structure (Ricklefs 1987).

More homogeneous environments such as forest plantations may have continuous modifications affecting the composition and structure of animal communities due to interactions between biotic and abiotic factors (Ganho & Marinoni 2005). Furthermore, species diversity may be related to the effective-functioning of the ecosystem (Loreau et al. 2001). Therefore, studies on the abundance of species in natural communities and their variation in time and space are important.

The increase of eucalyptus plantations in Brazil facilitates a larger number of native Lepidoptera to adapt to these exotic plant species, such as Eupseudosoma aberrans Schaus and Eupseudosoma involuta Sepp (Arctiidae), Automeris sp. Walker and Eacles imperialis Walker (Saturniidae), Oxydia vesulia Cramer, Sabulodes caberata Guenée and Thyrinteina arnobia (Stoll) (Geometridae) (Guedes et al. 2000; Zanuncio et al. 2006). Lepidoptera pests like T. arnobia are important to forestry because of population outbreaks and consequent damage in eucalyptus plantations in Brazil (Zanuncio et al. 2006).

The occurrence of Lepidoptera pests and species with the potential to acquire pest status has been defined in monitoring programs by forestry companies (Pereira et al. 2001; Zanuncio et al. 2001; Zanuncio et al. 2006) in different regions using light traps (Kitching et al. 2000; Osaki et al. 2011).

Lepidoptera can be dependent on plants in a community and most of them have some degree of host specificity (Dyer et al. 2007; Harrison & Berenbaum 2013). The spatial occurrence of these species may be limited to environments suitable for their development, which may have implications in monitoring and managing their populations.

The objective of this study was to evaluate and to compare the spatial distribution of species diversity of Lepidoptera across eucalyptus plantations in the Amazon region of Brazil.

Materials and Methods

Lepidoptera Sampling

The insects were collected in Eucalyptus urophylla S.T. Blake (Myrtaceae) plantations, which were 6 mo to 2 yr old at the beginning of the study (Table 1). Each area was monitored every 15 days from Sep 1992 to Aug 1997 with a light trap model Intral AL 012 (Clarke, Sao Paulo, Brazil), equipped with fluorescent black light bulb F15 T12 LN, with a wavelength of 290 nm to 450 nm powered by a 12-V and 55 A battery placed at 2 m height at the midpoint of each eucalyptus stand and operated from 6:00 P.M. to 6:00 A.M. of the next day. A plastic bag of 45 × 75 cm in width and length, respectively, with strips of newsprint and a bottle with ethyl acetate and a wick were attached to the bottom of the trap to hasten death and avoid excessive fraying of the insects. A distance of approximately 50 km separated the traps in Caracuru, Pacanari and Ponte Maria in Almerim municipality, Pará State and in Felipe, Laranjal do Jari municipality, Amapá State in the Amazonian region of Brazil.

The insects collected were sorted, packed and sent to the Laboratory of Biological Control of Insects, Department of Entomology, Federal University of Viçosa, in Viçosa, Minas Gerais State, Brazil. The specimens collected were identified based on the literature, and by comparison with those in the Regional Museum of Entomology/ UFV (UFVB), and by experts of the Center of Phytophagous Insect Identification of the Federal University of Paraná, in Paraná State, Brazil. The insects were deposited in the collection of the Regional Museum of Entomology/UFV.

Alpha Diversity

Richness is a measure of the number of species in an area, but may present systematic flaws (Ricklefs 1996). This index has been calculated with rarefaction methods to obtain the «expected» number of species according to the number of sampled individuals (Ramalho & Silva 2002). The first order Jackknife procedure is one of the more accurate nonparametric methods to express the richness of a community and to correcting its shortcomings (Palmer 1991). Comparisons between sampling efforts were conducted by correction using randomized cumulative species curves based on samples, after 100 randomizations calculated by the software Estimates version 8.2 (Colwell 2009), using the Statistica 9.0 (Statsoft 2009) analysis to compare the results.

Table 1.

Characterization of sampling sites of lepidopteran defoliators on eucalyptus in Caracuru, Pacanari and Ponte Maria, Pará State and Felipe, Amapá State, Brazil.


A species accumulation curve for each sampled site with the Jackkinfe estimator and values estimated at a confidence interval of 95% (Colwell & Coddington 1994) was made. The estimate by Jackknife is:


where: Sobs = is the total number of observed species in all samples; m = total number of samples.

Beta Diversity

The beta diversity indices with presence and absence data are still controversial (Wilson & Shmida 1984; Harrison et al. 1992) and with a wide variety of indexes. The approach of this study was based on dissimilarity measures estimated by the Jaccard index. The index is defined as:


where: Dij = is the measure of dissimilarity between the squares; i and j = the number of common species or genera; S. and S. = species richness of species or genera in each area.

The mean dissimilarity per point compared to the others was used as a measure of beta diversity. High values of this measure mean a place with very particular species composition and preservation.

Lepidopterans collected were divided in groups I, II and III, which consisted of primary pests, secondary pests and those with undefined importance to eucalyptus, respectively (Zanuncio et al. 2006).


For the eucalyptus plantations in Caracuru, Felipe, Pacanari and Ponte Maria, the respective numbers of lepidopteran individuals collected were 8,381, 1,010, 3,459 and 1,015 for the primary pests; 666, 324, 249 and 351 for the secondary ones and 3,195, 3,558, 4,034, and 5,615 for those species with undefined importance for the eucalyptus. The estimated value of the richness (Fig. 1), calculated by the Jackknife index, ranged from 10 to 11 species of group I; 9 to 10 species of group 11 and 378 to 409 species of group III, between the sampling sites, without differences per group between areas.

The species accumulation curves showed stability for the primary pests group between the 15th and 35th sampling and for the secondary ones in the 70th, 45th, 35th and 20th samplings in Caracuru, Felipe, Pacanari and Ponte Maria, respectively. The accumulation curves for the species with undefined importance to eucalyptus differed from those of other groups for the 4 sampling areas (Fig. 2). At the beginning of the sampling, the estimated species richness of this group ranged from 50 to 100 species and increased with a steep slope curve until approximately the 60th sample, when it slowly increased and tended to stabilize in the 4 areas.

The primary pest species were the same in all areas, and therefore, the beta diversity of this group was zero. Species diversity of group II was low (Table 2, Fig. 1) and similar in Caracuru, Pacanari and Ponte Maria, differing only in Felipe. Group III showed the highest beta diversity, possibly due to major differences in species richness, and the region of Felipe again showed the most difference between the areas (Table 2).

The dissimilarity of secondary pests differed between the areas except in Felipe, which differed by 5.88% from the others (Table 3). The species with undefined importance to eucalyptus plantations showed lower dissimilarity between Caracuru and Ponte Maria (14.88%) and with greater values between Felipe and Pacanari (21.64%) (Table 3).


The primary and secondary pest species collected were those commonly found in eucalyptus plantations in different regions of Brazil (Pereira et al. 2001; Zanuncio et al. 2003; Freitas et al. 2005; Zanuncio et al. 2006). This indicates that they are associated with alternative hosts, but have adapted to cultivated eucalyptus (Freitas et al. 2005; Pereira et al. 2009). Furthermore, forest plantations have lower diversity of plants and therefore can have lower numbers of natural enemies.

Fig. 1.

Estimated richness (Jackknife) for lepidopteran primary pests (A), secondary pests (B) and species with undefined importance to eucalyptus plantations (C) in Caracuru, Pacanari and Ponte Maria, Pará State and Felipe, Amapá State, Brazil. (The bars represent the 95% confidence interval).


The abundance of lepidopterans may be influenced by habitat type (Robinson et al. 2012); however, all of the areas studied were adjacent to E. urophylla plantations, which may have contributed to the herbivore and host specificity, as reported for other Brazilian regions (Pereira et al. 2001; Oliveira et al. 2005; Zanuncio et al. 2006).

Fig. 2.

Estimation of richness of lepidopteran species with undefined importance to Eucalyptus urophylla plan tations in Ponte Maria (A), Pacanari (B) and Caracuru (C), Pará State, and Felipe (D), Amapá State, Brazil.


The lower numbers of individuals of group I in Felipe and Ponte Maria and of species richness of the group III in Felipe are possibly related to the greater proximity of eucalyptus plantations to the native forest. This agrees with the lower number of lepidopteran pests found in E. cloeziana plantations with strips of native vegetation in Minas Gérais State, Brazil (Zanuncio et al. 1998b). Also, geographical factors such as area, distance and connectivity between sites affect the richness of lepidopteran species as reported in temperate environments (Bila et al. 2013). Furthermore, this can occur with natural enemy populations, suggesting that maintenance of areas or strips of native vegetation near eucalyptus plantations can be a reservoir of natural enemies such as hymenopteran parasitoids (Zanuncio et al. 2001). Protected and in post-successional stage forests may exhibit higher diversity and numbers of insects, because such areas have greater resources and varieties of microclimates (Merckx et al. 2012). This favors the migration of natural enemies to eucalyptus plantations where they can reduce pest populations (Zanuncio et al. 1998a; Teja & Roland 2004).

Table 2.

Beta diversity indices for lepidopteran primary pests (I), secondary pests (II) and species with undefined importance for eucalyptus (III) in the regions of caracuru, pacanari and ponte maria, Pará State And Felipe, Amapá State, Brazil.


The asymptotic curves of species accumulation showed that all primary and secondary pest species present in plantations were represented in all areas. The stabilization of these curves, over shorter periods, is attributed to the adaptation of these species to eucalyptus, as observed in other Brazilian regions (Freitas et al. 2005; Pereira et al. 2009). The cutting of native trees, whether managed or not, may favor lepidopteran pest species that feed on alternative hosts (Summerville et al. 2013) to migrate to the plantations, which justify the conservation of these areas.

Table 3.

Dissimilarities of alpha diversities calculated by the Jaccard Index for lepidopteran secondary pests (II) and species with undefined importance to eucalyptus (III) in the regions of caracuru, Pacanari and Ponte Maria, Pará State and Felipe, Amapá State, Brazil.


The lack of stabilization of species accumulation curves in short term for the species of group III may be caused by the low variability of plants and scarcity of alternative sources of food for lepidopterans in the plantation understory in the first months of planting. Moreover, it can be attributed to the smallest canopy volume of young plantations, because species richness may be positively correlated with tree cover (Houlihan et al. 2013).

The group III species may not feed on eucalyptus plants and, therefore, require other hosts, which would explain the greater effort, and the sampling period to stabilize the curve for this group. Rare lepidopteran species may be associated with plant species in areas with forest dominance or underbrush vegetation (Meehan et al. 2013). The high species diversity of this group may be related to vegetation diversity in native forests near the plantations, whose insect fauna can migrate to forest plantations (Zanuncio et al. 2001).

The higher richness and abundance of lepidopteran species of group III can be explained by the positive correlation with the size and distance of the native forest fragment from the eucalyptus plantation (Rosin et al. 2012). Areas with such plantations were surrounded by the Amazon forest with large trees, mainly in Caracuru and Pacanari, which may have increased the species diversity of group III at these sites.

The similarity between areas shows that a lower sampling effort was required to achieve the stabilization of species accumulation curves of the primary and secondary pests. Furthermore, the low dissimilarity between sampling sites indicates that the monitoring methodology was appropriate to represent the fauna of lepidopteran pests of this group of eucalyptus. This type of survey is important for the development of programs of integrated management aiming to control these insects (Maalik et al. 2013). The eucalyptus plantations, even at 50 km away from each other, have biotic and abiotic conditions without high variations, which contribute to the similar results between them.

The knowledge of the population dynamics and estimation of species richness are important strategies for monitoring defoliator lepidopterans of eucalyptus. The survey of primary and secondary pests of this plant can be concentrated in shorter periods to streamline the management and to reduce the costs of monitoring and control. This can be done because the primary and secondary pests are the same or with very low variations between the sampled sites.


To “Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)”, “Coordenação de Aperfeiçoamento de Pessoal de Nivel Superior (CAPES)” and “Fundação de Amparo à Pesquisa do Estado de Minas Gerais (FAPEMIG)” for financial support.



K. Bila , T. Kuras , J. Sipos , and P. Kindlmann 2013. Lepidopteran species richness of alpine sites in the High Sudetes Mts.: effect of area and isolation. J. Insect Conserv. 17: 257–267. Google Scholar


R. K. Colwell , and J. A. Coddington 1994. Estimating terrestrial biodiversity through extrapolation. Philos. Trans. R. Soc. B. 345: 101–118. Google Scholar


R. K. Colwell 2009. Estimates: Statistical estimation of species richness and shared species from samples. Version 8.2. User's Guide and application published at: Scholar


P. J. Devries , G. T. Austin , and N. H. Martin 2009. Estimating species diversity in a guild of Neotropical skippers (Lepidoptera: Hesperiidae) with artificial lures is a sampling problem. Insect Conserv. Diver. 2: 125–134. Google Scholar


L. A. Dyer , M. S. Singer , J. T. Lill , J. O. Stireman , G. L. Gentry , R. J. Marquis , R. E. Ricklefs , H. F. Greeney , D. L. Wagner , H. C. Morais , I. R. Diniz , T. A. Kursar and P. D. Coley 2007. Host specificity of Lepidoptera in tropical and temperate forests. Nature 448: 696–700. Google Scholar


F. A. Freitas , T. V. Zanuncio , J. C. Zanuncio , P. M. Conceição , M. C. Q. Fialho , and A. S. Bernardino 2005. Effect of plant age, temperature and rainfall on Lepidoptera insect pests collected with light traps in a Eucalyptus grandis plantation in Brazil. Ann. Forest Sci. 62: 85–90. Google Scholar


N. G. Ganho , and R. C. Marinoni 2005. Adiversidade inventarial de Coleoptera (Insecta) em uma paisagem antropizada do Bioma Araucária. Rev. Bras. Entomol. 49: 535–543. Google Scholar


L. Gimesi , R. Homoródi , A. Hirka , C. Szabóki , and L. Hufnagel 2012. The effect of climate change on the phenology of moth abundance and diversity. Appl. Ecol. Environ. Res. 10: 349–363. Google Scholar


R. N. C. Guedes , T. V. Zanuncio , J. C. Zanuncio , and A. G. B. Medeiros 2000. Species richness and fluctuation of defoliator Lepidoptera populations in Brazilian plantations of Eucalytus grandis as affected by plant age and weather factors. Forest Ecol. Mgt. 137: 179–184. Google Scholar


S. Harrison , S. J. Ross , and J. H. Lawton 1992. Beta diversity on geographic gradients in Britain. J. Anim. Ecol. 61: 151–158. Google Scholar


T. Harrison , and M. R. Berenbaum 2013. Moth diversity in three biofuel crops and native prairie in Illinois. Insect Sci. 20: 407–419. Google Scholar


J. K. Hill , and K. C. Hamer 1998. Using species abundance models as indicators of habitat disturbance in tropical forests. J. Appl. Ecol. 35: 458–460. Google Scholar


P. R. Houlihan , M. E. Harrison , and S. M. Cheyne 2013. Impacts of forest gaps on butterfly diversity in a Bornean peat-swamp forest. J. Asia-Pacific Entomol. 16: 67–73. Google Scholar


R. L. Kitching , A. G. Orr , L. Thalib , H. Mitchell , M. S. Hopkins , and A. W. Graham 2000. Moth assemblages as indicators of environmental quality in remnants of upland Australian rain forest. J. Appl. Ecol. 37: 284–297. Google Scholar


W. P. Lemos , F. S. Ramalho , J. E. Serrão , and J. C. Zanuncio 2003. Effects of diet on development of Podisus nigrispinus (Dallas) (Heteroptera: Pentatomidae), a predator of the cotton leafworm. J. Appl. Entomol. 127: 389–395. Google Scholar


M. Loreau , S. Naeem , P. Inchausti , P. Bengtsson , J. P. Grime , A. Hector , D. U. Hooper , M. A. Huston , D. Raffaelli , B. Schmid , D. Tilman , and D. A. Wardle 2001. Biodiversity and ecosystem functioning: current knowledge and future challenges. Science 294: 804–808. Google Scholar


J. E. Losey , and M. Vaughan 2006. The economic value of ecological services provided by insects. Bioscience 56: 311–323. Google Scholar


J. E. Losey , and M. Vaughan 2008. Conserving the ecological services provided by insects. American Entomol. 54: 113–115. Google Scholar


S. Maalik , S. A. Rana , H. A. Khan , and M. Ashfaq 2013. Diversity and abundance of lepidopteran populations from selected crops of district Faisalabad, Pakistan. Pakistan J. Agric. Sci. 50: 95–101. Google Scholar


T. D. Meehan , J. Glassberg , and C. Gratton 2013. Butterfly community structure and landscape composition in agricultural landscapes of the central United States. J. Insect Conserv. 17: 411–419. Google Scholar


T. Merckx , R. E. Feber , D. J. Hoare , M. S. Parsons , C. J. Kelly , N. A. D. Bourn , and D. W. Macdonald 2012. Conserving threatened Lepidoptera: Towards an effective woodland management policy in landscapes under intense human land-use. Biol. Conserv. 149: 32–39. Google Scholar


M. Nummelin 1998. Log-normal distribution of species abundances is not a universal indicator of rain forest disturbance. J. Appl. Ecol. 35: 454–457. Google Scholar


H. N. Oliveira , J. C. Zanuncio , E. P. P. Pedruzzi , and M. C. Espindula 2005. Rearing of Thyrinteina arnobia (Lepidoptera: Geometridae) on guava and Eucalyptus in Laboratory. Brazilian Arch. Biol. Technol. 48: 801–806. Google Scholar


K. Osaki , K. Sayama , A. Ueda , M. Ito , K. Tabuchi , and T. Hlronaga 2011. Short-term, efficient sampling strategies for estimating forest moth diversity using light traps. Ann. Entomol. Soc. America 104: 739–748. Google Scholar


M. W. Palmer 1991. Estimating richness species: the second order jacknife reconsidered. Ecology 72: 1512–1513. Google Scholar


J. M. M. Pereira , T. V. Zanuncio , J. C. Zanuncio , and D. Pratissoli 2001. Lepidoptera pests collected in Eucalyptus urophylla plantations during five years in Três Marias, State of Minas Gerais, Brazil. Rev. Biol. Trop. 49: 997–1006. Google Scholar


F. F. Pereira , T. V. Zanuncio , J. C. Zanuncio , D. Pratissoli , and M. T. Tavares 2008. Species of Lepidoptera defoliators of Eucalyptus as new host for the parasitoid Palmistichus elaeisis (Hymenoptera: Eulophidae). Brazilian Arch. Biol. Technol. 51: 259–262. Google Scholar


A. I. A. Pereira , C. R. S. Curvêlo , A. M. N. M. Guerra , G. S. Andrade , and J. C. Zanuncio 2009. Eucalyptus cloeziana as a new host to Hylesia paulex (Lepidoptera: Saturniidae) in Southeast Brazilian. Rev. Caatinga 22: 1–5. Google Scholar


M. Ramalho and M. Silva 2002. Flora oléfera e sua guilda de abelhas em uma comunidade de restinga tropical. Sitientibus, Sér. Ciênc. Biol. 2: 34–43. Google Scholar


R. E. Ricklefs 1987. Community diversity: relative roles of local and regional processes. Science 235: 167–171. Google Scholar


R. E. Ricklefs 1996. A economia da natureza. 3 ed. Guanabara Koogan, Rio de Janeiro, 470 pp. Google Scholar


N. Robinson , S. Armstead , and M. Deane Bowers 2012. Butterfly community ecology: The influences of habitat type, weather patterns, and dominant species in a temperate ecosystem. Entomol. Exp. Appl. 145: 50–61. Google Scholar


Z. M. Rosin , L Myczko, P. Skorka , M. Lenda , D. Moron , T. H. Sparks , and P. Tryjanowski 2012. Butterfly responses to environmental factors in fragmented calcareous grasslands. J. Insect Conserv. 16: 321–329. Google Scholar


Statsoft, Inc. 2009. Statistica (Data Analysis Software System), version 9.0.  www.statsoft.comGoogle Scholar


K. S. Summerville , and O. Crist 2008. Structure and conservation of lepidopteran communities in managed forests of northeastern North America: a review. Canadian Entomol. 140: 475–494. Google Scholar


K. S. Summerville , J. Lane , and D. Coward-Hauri 2013. Stability in forest lepidopteran communities: how sensitive are pest species to experimental forest management? Insect Conserv. Diver. 6: 265–275. Google Scholar


T. Teja , and B. Roland . 2004. Plant-insect interactions in fragmented landscapes. Annu. Rev. Entomol. 49: 405–30. Google Scholar


M. V. Wilson , and A. Shmida 1984. Measuring beta diversity with presence-absence data. J. Ecol. 72:1055–1064. Google Scholar


T. V. Zanuncio , J. C. Zanuncio , M. M. M. Miranda , and A. G. B. Medeiros 1998a. Effect of plantation age on diversity and population fluctuation of Lepidoptera collected in Eucalyptus plantations in Brazil. Forest Ecol. Mgt. 108: 91–98. Google Scholar


J. C. Zanuncio , J. A. Mezzomo , R. N. C. Guedes , and A. C. Oliveira 1998b. Influence of strips of native vegetation on Lepidoptera associated with Eucalyptus cloeziana in Brazil. Forest Ecol. Mgt. 108: 85–90. Google Scholar


J. C. Zanuncio , R. N. C. Guedes , T. V. Zanuncio , and A. S. Fabres 2001. Species richness and abundance of defoliating Lepidoptera associated with Eucalyptus grandis in Brazil and their response to plant age. Austral Ecol. 26: 582–589. Google Scholar


J. C. Zanuncio , T. V. Zanuncio , F. A. Freitas , and D. Pratissoli 2003. Population density of Lepidoptera in an plantation of Eucalyptus urophylla in the state of Minas Gerais, Brazil. Anim. Biol. 53: 17–26. Google Scholar


T. V. Zanuncio , J. C. Zanuncio , F. A. Freitas , D. Pratissoli , C. A. Z. Sediyama , and V. P. Maffia 2006. Main lepidopteran pest species from a eucalytpus plantation in Minas Gerais, Brazil. Rev. Biol. Trop. 54: 553–560. Google Scholar
José Cola Zanuncio, Pedro Guilherme Lemes, Germi Porto Santos, Carlos Frederico Wilcken, Bruno Zaché, Rosenilson Pinto, and José Eduardo Serrão "Alpha and Beta Diversity of Lepidoptera in Eucalyptus Plantations in the Amazonian Region of Brazil," Florida Entomologist 97(1), 138-145, (1 March 2014).
Published: 1 March 2014
entomologia florestal
forest entomology
pragas primárias
Back to Top