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Insect galls and associated fauna in two areas of Cerrado sensu stricto in the State of Bahia, Brazil

Abstract

This study inventoried and characterized the richness of galling insects based on gall morphotypes and their host plants in two Cerrado sensu stricto areas of Caetité municipality in Bahia State, Brazil, to aid the identification of galling insects and their host plants, as well as to contribute to the knowledge and conservation of local biodiversity. The survey was conducted in the Moita dos Porcos archaeological site and João Barroca Farm site, adopting the random walking methodology for sampling, during 12 months. We recorded 98 gall morphotypes on 42 plant species belonging to 36 genera and 22 families. Leguminosae, Malpighiaceae and Myrtaceae demonstrated the greatest richness of galls, and the Copaifera langsdorffii was the super-host species, with 16 gall morphotypes. Most galls occur on leaves, and may be globoid, glabrous, grouped, and are usually unilocular, and brown. The galling insects identified belonged to Coleoptera, Diptera, Lepidoptera, and Thysanoptera. Eight plant host species and eight gall morphotypes were recorded for the first time in Cerrado areas in Brazil. The areas surveyed demonstrated high richness of gall morphotypes and host plants, evidencing the importance of studying and preserving different areas of the same biome.

Key words
Copaifera galls; gall morphotypes; Malpighiaceae; savanna

INTRODUCTION

Brazilian Cerrado is a hostpost of biodiversity, which is formed by mosaic of different phytophysiognomy, demonstrating elevated levels of species richness. It hosts more than 12,330 plant species (BFG 2018BFG - THE BRAZIL FLORA GROUP. 2018. Brazilian Flora 2020: innovation and collaboration to meet Target 1 of the Global Strategy for Plant Conservation (GSPC). Rodriguésia 69: 1513-1527., 2021BFG - THE BRAZIL FLORA GROUP. 2021. Brazilian Flora 2020 project - Projeto Flora do Brasil 2020. v393.274. Instituto de Pesquisas Jardim Botanico do Rio de Janeiro. Dataset/Checklist. doi:10.15468/1mtkaw.) and one third of Brazilian biodiversity, with a high level of endemism, making it the most biodiverse savanna in the world (Klink & Machado 2005KLINK CA & MACHADO RB. 2005. Conservation of the brazilian cerrado. Conserv Biol 19: 707-713.). In the state of Bahia, the Cerrado covers an area of approximately 9.1 million hectares (Faleiro 2015FALEIRO FG. 2015. Ecossistema do cerrado na Bahia: possibilidades de desenvolvimento agrícola sustentável e sugestões de linhas de pesquisa. In: Baiardi A (Ed), Potencial de agricultura sustentável na Bahia: possibilidades e sugestões de linhas de pesquisa por ecossistemas. Salvador: EDUFBA.) distributed mainly in the western region of the state (Harley 1995HARLEY RM. 1995. Introduction. 1-853p. In: Stannard BL, Harvey YB & Harley RM (Eds), Flora of the Pico das Almas, Chapada Diamantina - Bahia, Brazil. Kew, Royal Botanic Gardens.). In addition, the Cerrado of Bahia is also distributed in higher regions forming small patches interspersed by Campos Rupestres, Caatinga and Seasonal Forests and transition areas, as occurs in Chapada Diamantina (Harley et al. 2005HARLEY RM ET AL. 2005. Cerrado, p. 121-152. In: Juncá FA, Funch L & Rocha W (Eds), Biodiversidade e conservação da Chapada Diamantina. Brasília: MMA.), and Serra Geral of the Caetité municipality (Bahia State, Brazil).

The Brazilian Cerrado is also one of the most threatened biomes, due to continuing deforestation. It is estimated that 43% of its native vegetation has already been removed or transformed (MMA 2015MMA. 2015. Mapeamento do uso e cobertura do Cerrado: Projeto Terra Class Cerrado. Available at: http://www.mma.gov.br/images/arquivo/80049/Cerrado/publicacoes/Livro%20EMBRAPA-WEB-1-TerraClass%20Cerrado.pdf (Accessed April 8, 2018).
http://www.mma.gov.br/images/arquivo/800...
). The Cerrado areas of the Caetité municipality have been subjected to constant environmental impacts (Rodrigues et al. 2017RODRIGUES OF, SILVA JJF & NUNES PIC. 2017. Parecer da Nascente do Riacho Pedra de Ferro nos municípios de Caetité e Pindaí-Bahia. II Simpósio Bahiano de Geografia Agrária: entre a teoria e prática, articulações e resistências. Julho 03-05, Salvador, Bahia, p. 1-12.) due to iron ore and limestone rock extraction (DNPM 2014DNPM - DEPARTAMENTO NACIONAL DE PESQUISA MINERAL. 2014. Salvador: DNPM. http://www.dnpm.gov.br/acesso-a-informacao/legislacao/portarias-do-diretor-geral-do-dnpm/portarias-do-diretor-geral/portaria-no-144-em-03-05-2007-do-diretor-geral-do-dnpm. (Accessed March 1, 2018).
http://www.dnpm.gov.br/acesso-a-informac...
), the construction of wind farms (Prudente et al. 2017PRUDENTE TA, ANJOS JASA & SOARES AGL. 2017. Geração de energia elétrica por fonte eólica. Bahia Análise & Dados, Salvador, 27: 28-48, como atua o licenciamento ambiental no estado da Bahia, EISSN 2595-2064.), and amethyst mining.

Cerrado vegetation has several interactions among plants and herbivores (Ribeiro & Fernandes 2000RIBEIRO SP & FERNANDES GW. 2000. Interações entre insetos e plantas no Cerrado: teoria e hipóteses de trabalho. In: Martins RP, Lewinsohn TM & Barbeitos MS (Eds), Ecologia e comportamento de insetos. Oecologia Brasiliensis, Rio de Janeiro, Brasil, p. 299-320., Furtado et al. 2003FURTADO, AG, URBANETZ C, VIANEI LK, SÁ R, CANDIDO PC, ANJOS LA, CERQUEIRA MR & RAIMUNDO RLG. 2003. A frequência de Plantas Herviboras difere entre uma área de Cerrado e uma área Adjacente com Pertubação Antrópica? UNICAMP. https://www2.ib.unicamp.br/profs/fsantos/relatorios/ne211r4a2003.pdf. (Accessed April 8, 2018).
https://www2.ib.unicamp.br/profs/fsantos...
, Cintra et al. 2020CINTRA CF ET AL. 2020. Plant-galling insect interactions: a dataset of host plants and their gall-inducing insects for the Cerrado. Ecology: e03149.). Among the different forms of herbivory, the endophytic habit of galling insects is by far the most sophisticated (Shorthouse et al. 2005SHORTHOUSE, JD, WOOL D & RAMAN A. 2005. Gall-inducing insects – Nature’s most sophisticated herbivores. Basic Appl Ecol 6: 407-411.). Galling insects are capable of inducing galls through disordered processes of hyperplasia, hypertrophy, and cellular differentiation in plant tissues (Ferreira & Isaias 2013FERREIRA BG & ISAIAS RMS. 2013. Developmental stem anatomy and tissue redifferentiation induced by a galling Lepidoptera on Marcetia taxifolia (Melastomataceae). Botany 91: 752-760.). The structures resulting from those interactions provide shelter for the gall-inducing insect against abiotic and biotic factors, allowing its successful development, and energetic resources for nutrition of the inducers (Price et al. 1987PRICE PW, FERNANDES GW & WARING GL. 1987. Adaptive Nature of Insect Galls. Environ Entomol 16: 15-24., Stone & Schönrogge 2003STONE GN & SCHÖNROGGE N. 2003.The adaptive significance of insect gall morphology. Trends Ecol Evol 18: 512-522.).

The Brazilian Cerrado has been the subject of in-depth studies on the richness of galls, mainly in state of Minas Gerais (e.g., Gonçalves-Alvim & Fernandes 2001GONÇALVES-ALVIM SJ & FERNANDES GW. 2001. Biodiversity of galling insects: historical, community and habitat effects in four Neotropical savannas. Biod Conserv 10: 79-98., Urso-Guimarães et al. 2003URSO-GUIMARÃES MVC, SCARELI-SANTOS C & BONIFÁCIO-SILVA A. 2003. Occurrence and characterization of entomogen galls in plants from natural vegetation areas in Delfinópolis, MG, Brazil. Braz J Biol 63: 705-715., Carneiro et al. 2009aCARNEIRO MAA, BORGES RAX, ARAÚJO APA & FERNANDES GW. 2009a. Insetos indutores de galhas da porção Sul da Cadeia do Espinhaço Minas Gerais, Brasil. R Bras Entomol 53: 570-592., Araújo & Guilherme 2012ARAÚJO WS & GUILHERME FAG. 2012. Distribuição de insetos galhadores em diferentes formações vegetais e paisagens do cerrado brasileiro. Biosci J 28: 810-819., Coelho et al. 2013COELHO MS, CARNEIRO MAA, BRANCO C & FERNANDES GW. 2013. Insetos indutores de galhas da Serra do Cabral, Minas Gerais, Brasil. Biota Neotrop 13: 102-109., Cintra et al. 2020CINTRA CF ET AL. 2020. Plant-galling insect interactions: a dataset of host plants and their gall-inducing insects for the Cerrado. Ecology: e03149.). The richness of gall studies in the Cerrado of Bahia State has been little studied; only five has yet been undertaken in the municipalities of Caetité (Nogueira et al. 2016NOGUEIRA, RM, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2016. Insect galls from Serra Geral, Caetité, BA, Brazil. Biota Neotrop 16: e20150035., Vieira et al. 2018VIEIRA LG, NOGUEIRA RM, COSTA EC, CARVALHO- FERNANDES SP & SANTOS-SILVA J. 2018. Insect galls in rupestrian field and cerrado stricto sensu vegetation in Caetité, Bahia, Brasil. Biota Neotrop 18: e20170402., Silva et al. 2018SILVA AF, NOGUEIRA RM, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2018. Occurrence and characterization of entomogenic galls in an area of Cerrado sensu stricto and Gallery forest of the state of Bahia, Brazil. An Acad Bras Cienc 90: 2903-2919., Santana et al. 2020SANTANA CAGS, COSTA EC, CARVALHO-FERNANDES S & SANTOS-SILVA J. 2020. Insect galls and their host plants in gallery forest in Bahia State, Brazil. Braz J Bot 43: 989-998.) and Barreiras (Lima & Calado 2018LIMA VP & CALADO D. 2018. Morphological characterization of insect galls and new records of associated invertebrates in a Cerrado area in Bahia State. Braz J Biol 78: 636-643.). These studies in the Cerrado of Bahia recorded a total of 144 different types of galls in 103 plant species.

Studies of galling insect richness have demonstrated the usefulness of that insect guild as a measure of environmental conservation and quality (Santos et al. 2012SANTOS BB, RIBEIRO BA, SILVA TM & ARAÚJO WS. 2012a. Galhas de insetos em uma área de cerrado sentido restrito na região semi-urbana de Caldas Novas (Goiás, Brasil). Rev Bras Bioci 10: 439-445., Santana & Isaias 2014SANTANA AP & ISAIAS RMS. 2014. Galling insects are bioindicators of environmental quality in a Conservation Unit. Acta Bot Bras 28: 594-608., Brito et al. 2018BRITO GP, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2018. Riqueza de galhas de insetos em sítios de Caatinga com diferentes graus de impacto antropogênico, Bahia, Brasil. Iheringia, Sér Zool 108: 1-9.). The entomofauna associated with galls responds to environmental disturbances, with resulting losses of species richness and abundance (which also impact their natural enemies) (Oliveira 2009OLIVEIRA JC. 2009. Viabilidade de espécies galhadoras (Diptera, Cecidomyiidae) e parasitóides (Hymenoptera) associadas à Guapira opposita (Vell.) (Nyctaginaceae) como bioindicadores da qualidade ambiental. Tese de Doutorado, Universidade Federal do Rio de Janeiro, Rio de Janeiro.). As such, inventories of gall-inducing insect richness can assistance in urban planning, design, and management (Julião et al. 2005JULIÃO GR, FERNANDES W, NEGREIROS D, BEDÊ L & ARAÚJO RC. 2005. Insetos galhadores associados a duas espécies de plantas invasoras de áreas urbanas e peri-urbanas. R Bras Entomol 49: 97-106.) as well as for environmental monitoring and conservation activities (Santana & Isaias 2014SANTANA AP & ISAIAS RMS. 2014. Galling insects are bioindicators of environmental quality in a Conservation Unit. Acta Bot Bras 28: 594-608., Melo-Júnior et al. 2018MELO-JÚNIOR JCF, ISAIAS RMS, BOEGER MRT, ARRIOLA IA & MATILDE-SILVA M. 2018. Diversidade de galhadores nas restingas do ecossistema Babitonga, Santa Catarina, Brasil. Revista Cepsul - Biodiversidade e Conservação Marinha 7: eb2018003.). Here, we realized an inventory of the richness of galling insects in two Cerrado sensu stricto areas of the Caetité municipality (Bahia) and a similarity analysis between areas based on gall morphotypes and their host plants to contribute to the knowledge and conservation of local biodiversity.

MATERIALS AND METHODS

Study area

The study was carried out in two localities of Cerrado sensu stricto vegetation in the municipality of Caetité, Bahia State, Brazil: João Barroca Farm (JB) (14°19’23.96” S and 42°33’’7.91” W) situated about 40 km of Caetité’s center, and the Moita dos Porcos archaeological site (MP) (14°10’1.52” S and 42°31’’16.05” W) approximately 15 km from the city center. The areas studied were selected on the basis of accessibility for sampling, the distance from previously sampled areas, and the presence of preserved vegetation (Costa et al. 2014aCOSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2014a. Galhas entomógenas associadas à Leguminosae do entorno do riacho Jatobá, Caeitité, Bahia, Brasil. R Bras Bioci 12: 115-120., b, Nogueira et al. 2016NOGUEIRA, RM, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2016. Insect galls from Serra Geral, Caetité, BA, Brazil. Biota Neotrop 16: e20150035., Vieira et al. 2018VIEIRA LG, NOGUEIRA RM, COSTA EC, CARVALHO- FERNANDES SP & SANTOS-SILVA J. 2018. Insect galls in rupestrian field and cerrado stricto sensu vegetation in Caetité, Bahia, Brasil. Biota Neotrop 18: e20170402., Silva et al. 2018SILVA AF, NOGUEIRA RM, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2018. Occurrence and characterization of entomogenic galls in an area of Cerrado sensu stricto and Gallery forest of the state of Bahia, Brazil. An Acad Bras Cienc 90: 2903-2919., Santana et al. 2020SANTANA CAGS, COSTA EC, CARVALHO-FERNANDES S & SANTOS-SILVA J. 2020. Insect galls and their host plants in gallery forest in Bahia State, Brazil. Braz J Bot 43: 989-998.). The JB comprises approximately 105 hectares of preserved area at 950 m elevation, while the MP covers approximately 300 hectares of preserved area at 920 m elevation. The vegetation is composed of many herbaceous and woody species, with a palm (Syagrus werdermannii Burret, Arecaceae) and sparse trees from 2 to 3 m tall (e.g., Hymenaea courbaril L., Leguminosae). The soil is sandy to sandy with rock outcrops on the higher elevation sites (Alves 2008ALVES JES. 2008. Mapeamento Geológico e Análise Estrutural Multiescalar do Cinturão de Dobramentos e Cavalgamentos da Serra do Espinhaço Setentrional, Caetité, Bahia. Monografia (Bacharelado em Geologia) - Instituto de Geociências, Universidade Federal da Bahia, Salvador, 45 p. (Unpublished).). The regional climate is Aw (Alvares et al. 2013ALVARES CA, STAPE JL, SENTELHAS PC, GONÇALVES JLM & SPAROVEK G. 2013. Köppen’s climate classification map for Brazil. Meteorol Z 22: 711-728.), with a mean annual temperature of 21.4°C and mean annual rainfall of 862 mm (IBGE 2015IBGE - INSTITUTO BRASILEIRO DE GEOGRAFIA E ESTATÍSTICA. 2015. Manuais técnicos em geociências: manual técnico da vegetação brasileira. Sistema fitogeográfico. Inventário das formações florestais e campestres. Técnicas e manejo de coleções botânicas e procedimentos para mapeamentos. 2ª ed., IBGE, Rio de Janeiro, 271 p.).

Sampling method

The Cerrado vegetation was examined during 12 months, between May 2016 to April 2017 throughout the MP site and between August 2017 to July 2018 at the JB site, adopting the random walking methodology for sampling (Julião et al. 2002JULIÃO GR, AMARAL ME & FERNANDES GW. 2002. Galhas de insetos e suas plantas hospedeiras no Pantanal Sul-Matogrossense. Naturalia 27: 47-74., Oliveira & Maia 2005OLIVEIRA JC & MAIA VC. 2005. Ocorrência e caracterização de galhas de insetos na restinga de Grumari (Rio de Janeiro, RJ, Brasil). Arq Mus Nac 63: 669-675., Coelho et al. 2009COELHO MS, ALMADA ED, FERNANDES GW, CARNEIRO MAA, SANTOS RM, QUINTINO AV & SANCHEZ-AZOFEIFA A. 2009. Gall inducing arthropods from a seasonally dry tropical forest in Serra do Cipó, Brazil. Rev Bras Entomol 53: 404-414.). In these areas, the galls and the host plants were collected once a month by two people working for four person-hours along pre-existing trails, totaling 96 hours of total collecting efforts. All plant architectural types (herbaceous, shrub, arboreal, tree and vines) up to 2 m tall were inspected. Each gall morphotype was photographed in field, and characterized based on shape, color, presence or absence of trichomes, number of internal chambers (Isaias et al. 2013ISAIAS RMS, CARNEIRO RGS, OLIVEIRA DC & SANTOS JC. 2013. Illustrated and Annotated Checklist of Brazilian Gall Morphotypes. Neotrop Entomol 42: 230-239.). Specimens of the host plants were collected, pressed, and deposited in the Caetité Collection of the HUNEB herbarium. The plants were identified by consulting the taxonomic literature and contacting botanical specialists, and by comparisons with herbarium collections at the Universidade do Estado da Bahia (HUNEB, Caetité collection) and the Universidade Estadual de Feira de Santana (HUEFS). Plant nomenclature was verified in the Flora do Brasil 2020 (www.floradobrasil.jbrj.gov.br) and, the names are presented in alphabetical order by family, following APG IV (2016)APG IV. 2016. An update of the Angiosperm Phylogeny Group classification for the orders and families of flowering plants: APG IV. Bot J Linn Soc 181: 1-20.. The circumscription of the Leguminosae family was based on classification proposed by LPWG (2017)LPWG - THE LEGUME PHYLOGENY WORKING GROUP. 2017. A community-endorsed phylogenetic classification of the Leguminosae, including a new densely-sampled phylogeny of the family. Taxon 66: 44-77..

The samples of each gall morphotypes collected in the field were analyzed in laboratory. Galls were dissected under a stereomicroscope to retrieve any larvae of the gall-inducing insects and/or associated fauna, as well as observation the number of larval chamber. To obtain adults, samples of each gall morphotype were held separately in labeled plastic containers (lined with paper) and inspected daily. All of the insects obtained were conserved in 70% alcohol and sent to be identified at the Diptera Laboratory of the National Museum at the Universidade Federal do Rio de Janeiro.

Statistical Analysis

Sørensen’s similarity index (S= 2c/a+b) (Sørensen 1948SØRENSEN TA. 1948. A method of establishing groups of equal amplitude in plant sociology based on similarity of species content, and its application to analyses of the vegetation on Danish commons. Kongelige Danske videnskabernes selskab. Biol Skr 5: 1-34.) was used to compare the two localities in relation to the host plants (c = number of host plant species common to JB and MP, a = number of species in JB and b = number of species in MP) and gall morphotypes (c= number of gall morphotypes common to JB and MP, a = number of gall morphotypes in JB and b = number of gall morphotypes in MP).

RESULTS

We recorded 98 gall morphotypes on 42 plant species belonging to 36 genera and 22 families (Table I; Figures 1-5). Galls were recorded for the first time on the plant species Alchornea tiliifolia (Benth.) Müll. Arg. (Euphorbiaceae, Fig. 1m), Byrsonima correifolia A. Juss. (Malpighiaceae, Fig. 4c), Dalbergia acuta Benth. (Leguminoseae-Papilionoideae, Fig. 3m), Erythroxylum stipulosum Plowman (Erythoxylaceae, Fig. 1l), Eugenia lucidifolia Barb. Rodr. (Myrtaceae, Fig. 5b), Pseudobrickellia brasiliensis (Spreng.) R. M. King & Rob. (Asteraceae, Fig. 1h), Senna cana (Nees & Mart.) H. S. Irwin & Barneby var. cana (Leguminoseae- Caesalpinioideae, Fig. 2f), and Lippia origanoides Kunth (Verbenaceae, Fig. 5p).

Figure 1
Insect galls in two areas of Cerrado sensu stricto vegetation in Caetité, Bahia State, Brazil. a-b. Anacardium humile; c. Annonaceae Indet. d. Annona leptopetala; e-f.Duguetia furfuracea; g. Moquiniastrum paniculatum; h. Pseudobrickellia brasiliensis; i. Maytenus sp.; j. Combretum leprosum; k. Erythroxylum suberosum; l. Erythroxylum stipulosum; m. Alchornea tiliifolia; n. Manihot tripartita; o. Ocotea lancifolia;p-r. Calliandra dysantha; s. Calliandra macrocalyx; t. Mimosa gemmulata.
Figure 2
Insect galls in two areas of Cerrado sensu stricto vegetation in Caetité, Bahia State, Brazil. a-d. Mimosa gemmulata; e. Senegalia langsdorffii; f. Senna cana var. cana; g-i. Bauhinia acuruana; j-l. Bauhinia pulchella; m-t. Copaifera langsdorffii.
Figure 3
Insect galls in two areas of Cerrado sensu stricto vegetation in Caetité, Bahia State, Brazil. a-h. Copaifera langsdorffii; i. Copaifera luetzelburgii; j-k. Hymenaea courbaril; l. Andira parvifolia; m. Dalbergia acuta; n. Dalbergia miscolobium; o. Struthanthus sp.; p-q. Malpighiaceae Indet. 1; r. Malpighiaceae Indet. 2; s. Malpighiaceae Indet. 3.; t. Malpighiaceae Indet. 4.
Figure 4
Insect galls in two areas of Cerrado sensu stricto vegetation in Caetité, Bahia State, Brazil. a-b. Banisteriopsis malifolia; c. Byrsonima correifolia; d-e. Byrsonima gardneriana; f-h. Byrsonima sericea; i. Byrsonima sp.; j. Diospyros sp. k. Diplopterys pubipetala; l. Stigmaphyllon paralias; m. Helicteres sp.; n-o. Moraceae Indet. 1.; p. Myrtaceae Indet. 1; q. Myrtaceae Indet. 2; r. Myrtaceae Indet. 3; s. Eugenia sp.; t. Eugenia dysenterica.
Figure 5
Insect galls in two areas of Cerrado sensu stricto vegetation in Caetité, Bahia State, Brazil. a. Eugenia dysenterica; b. Eugenia lucidifolia; c-e. Eugenia punicifolia; f-g. Myrcia tomentosa; h. Guapira laxa; i-j. Ouratea semiserrata; k. Ouratea sp.; l. Turnera harleyi; m. Roupala montana; n. Rubiaceae Indet.; o. Trigonia nivea; p. Lippia origanoides; q-r. Qualea parviflora.
Table I
Insect galls of areas of Cerrado sensu stricto vegetation in the municipality of Caetité, Bahia State, Brazil. Abbreviations: JB, the João Barroca farm; MP, the Moita dos Porcos Archaeological Site.

A total of 73 gall morphotypes were found on the JB farm on 35 plant species belonging to 31 genera and 20 families (Table I). The species of the families Leguminosae, Malpighiaceae and Myrtaceae hosted the greatest gall richness, with 31, nine, and nine morphotypes, respectively. The plant genera with the greatest richness of gall morphotypes were Copaifera L. (Leguminosae-Detarioideae) (n = 13, n = 2 host species) and Byrsonima Rich. ex Kunth (Malpighiaceae) (n = 7, n = 4 host species). The super-host species with the greatest richness of gall morphotypes was Copaifera langsdorffii Desf (n = 12 gall morphotypes; Figs. 2m-o, 2q-t, 3a-e).

On the MP archaeological site, 40 gall morphotypes were found on 29 plant species belonging to 18 genera and 13 families (Table I). The plant families that hosted the greatest richness of gall morphotypes were Leguminosae and Malpighiaceae (n = 16 and n = 8, respectively). The plant genera with the greatest richness of galls were Copaifera L. (n = 10 gall morphotypes, n = 2 host species) and Byrsonima Rich. ex Kunth (n = 5 gall morphotypes, n = 3 host species). The super-host species with the greatest richness of gall morphotypes was Copaifera langsdorffii (n = 9 gall morphotypes; Figs. 2m-n, p, r, t, 3a, f-h).

The galls were found only on vegetative organs: leaves (n = 88, 57 in JB and 32 in MP), stems (n = 23, 15 in JB and eight in MP), and buds (n = 4 in JB). Most gall morphotypes occurred on a single plant organ; only one gall morphotype induced on Moquiniastrum paniculatum (Less.) G. Sancho (Asteraceae) was observed on both stems and leaves (Table I, Fig. 1g).

The most frequent gall shapes were globoid (n = 54, 32 in JB and 22 in MP), lenticular (n = 23, 15 in JB and 8 in MP), and fusiform (n = 12, 7 in JB and 5 in MP). Most galls were glabrous (n = 101, 67 in JB and 34 in MP), unilocular (n = 94, 64 in JB and 30 in MP), and solitary (n = 58, 41 in JB and 17 in MP) or grouped (n = 55, 32 in JB and 23 in MP). Gall color were green, brown, red, yellow, orange, gray, white, black or purple, being the brown color the most frequent (n = 44, 26 in JB and 18 in MP). The globoid leaf galls of Combretum leprosum Mart. (Combretaceae) could be green, yellow (Fig. 1j) red, or brown.

The inducer insects that emerged (from only 33 gall morphotypes) belonged to the orders Diptera, Cecidomyiidae (n = 27, 19 in JB, eight in MP), Lepidoptera (n = 2 in JB), Thysanoptera (n = 1 in JB), and Coleoptera (n = 1 in MP). The associated fauna was found in 17 gall morphotypes (n = 13 in JB, 10 in MP), and composed by parasitoids (Hymenoptera, n = 9, 9 in JB, four in MP), predators (Araneae, n = 3, one in JB, three in MP), inquilines (Hemiptera [n = 2, one in JB, one in MP] and Thysanoptera [n = 2, one in JB, one in MP]), and successors (Formicidae n = 1 in JB and MP).

The Sørensen’s index values indicated high similarity in host plants between JB farm and MP archaeological site (S=0.66). These localities shared 15 host plant species (Table I). In relation to the morphotypes galls, the similarity is low (S=0.36), with only 15 gall morphotypes common to both areas, showing that these localities differed in relation to the gall composition species.

DISCUSSION

The gall richness in JB and MP were high in comparison to other areas with Cerrado sensu stricto vegetation (Araújo et al. 2007ARAÚJO WS, GOMES-KLEIN VL & SANTOS BB. 2007. Galhas Entomógenas Associadas à Vegetação do Parque Estadual da Serra dos Pireneus, Pirenópolis, Goiás, Brasil. R Bras Bioci 5: 45-47., Urso-Guimarães et al. 2003URSO-GUIMARÃES MVC, SCARELI-SANTOS C & BONIFÁCIO-SILVA A. 2003. Occurrence and characterization of entomogen galls in plants from natural vegetation areas in Delfinópolis, MG, Brazil. Braz J Biol 63: 705-715., Coelho et al. 2013COELHO MS, CARNEIRO MAA, BRANCO C & FERNANDES GW. 2013. Insetos indutores de galhas da Serra do Cabral, Minas Gerais, Brasil. Biota Neotrop 13: 102-109., Nogueira et al. 2016NOGUEIRA, RM, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2016. Insect galls from Serra Geral, Caetité, BA, Brazil. Biota Neotrop 16: e20150035.), corroborating other studies that indicate that the Cerrado has the richest fauna of galling insects in Brazil (Araújo 2018ARAÚJO WS. 2018. 30 years of research o insect galls in Brazil: ascientometric review. Pap Avulsos Zool 58: e20185834., Cintra et al. 2020CINTRA CF ET AL. 2020. Plant-galling insect interactions: a dataset of host plants and their gall-inducing insects for the Cerrado. Ecology: e03149.).

The plant families with the greatest numbers of species in a given area generally correspond to those that host the greatest gall richness (Araújo et al. 2014ARAÚJO WS, CUEVAS-REYES P & GUILHERME FAG. 2014. Local and regional determinants of galling-insect richness in Neotropical savanna. J Trop Ecol 30: 269-272., Santos-Silva & Araújo 2020SANTOS-SILVA J & ARAÚJO TJ 2020. Are Fabaceae the principal super- hosts of galls in Brazil? An Acad Bras Cienc 92: e20181115.). Leguminosae, Malpighiaceae and Myrtaceae were the main host plant families of galls in the two Cerrado s.s. areas, a result similar to reports of other inventories realized in the Bahia Cerrado (Nogueira et al. 2016NOGUEIRA, RM, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2016. Insect galls from Serra Geral, Caetité, BA, Brazil. Biota Neotrop 16: e20150035., Vieira et al. 2018VIEIRA LG, NOGUEIRA RM, COSTA EC, CARVALHO- FERNANDES SP & SANTOS-SILVA J. 2018. Insect galls in rupestrian field and cerrado stricto sensu vegetation in Caetité, Bahia, Brasil. Biota Neotrop 18: e20170402.). Those botanical families together with Asteraceae and Melastomataceae hosting a rich diversity of gall-inducing insects in the Cerrado (n = 468 gall morphotypes), with many species bearing galls (n = 263 spp.) (Cintra et al. 2020CINTRA CF ET AL. 2020. Plant-galling insect interactions: a dataset of host plants and their gall-inducing insects for the Cerrado. Ecology: e03149.).

In addition to those super-host plant families, gall richness can be influenced by presence of super-host species that hosted more than double the number of gall morphotypes compared to other species (Mendonça 2007MENDONÇA MS. 2007. Plant diversity and galling arthropod diversity searching for taxonomic patterns in an animal-plant interaction in the neotropics. Bol Soc Argent Bot 42: 347-357., Araújo et al. 2013ARAÚJO WS, SCARELI-SANTOS C, GUILHERME FAG & CUEVAS-REYES P. 2013. Comparing galling insect richness among Neotropical savannas: effects of plant richness, vegetation structure and super-host presence. Biodivers Conserv 22: 1083-1094.), as is evidenced to Copaifera langsdorffii is this study. This species is frequent in the study area and is considered one of the principal super-hosts of galls in the Brazilian Cerrado (Costa et al. 2010COSTA FV, FAGUNDES M & NEVES FS. 2010. Arquitetura da planta e diversidade de galhas associadas a Copaifera langsdorffii (Fabaceae). Austral Ecol 20: 9-17., Lima & Calado 2018LIMA VP & CALADO D. 2018. Morphological characterization of insect galls and new records of associated invertebrates in a Cerrado area in Bahia State. Braz J Biol 78: 636-643., Fagundes et al. 2018FAGUNDES M, XAVIER RCF, FARIA ML, CUEVAS-REYES P, LOPES LG & REIS-JUNIOR R. 2018. Plant phenological asynchrony and community structure of gall-inducing insects in a super-host tropical tree species. Ecol Evol 8: 10687-10697.). According to Araújo et al. (2013)ARAÚJO WS, SCARELI-SANTOS C, GUILHERME FAG & CUEVAS-REYES P. 2013. Comparing galling insect richness among Neotropical savannas: effects of plant richness, vegetation structure and super-host presence. Biodivers Conserv 22: 1083-1094., the plant species richness explains more than 49 % of the gall inducing insect species richness in the Neotropical savannas, because their important role in the attraction of natural enemies and adaptive radiation of galling species.

Galls induced principally on leaves followed by stems is similar to the patterns seen throughout Brazil (Fernandes & Negreiros 2006FERNANDES GW & NEGREIROS D. 2006. A comunidade de insetos galhadores de RPPN Fazenda Bulcão, Aimorés, Minas Gerais, Brasil. Lundiana 7: 111-120., Santos et al. 2011bSANTOS JC, ALMEIDA-CORTEZ JS & FERNANDES GW. 2011b. Richness of gall-inducing insects in the tropical dry forest (caatinga) of Pernambuco. Rev Bras Ent 55: 45-54., 2012a, Toma & Mendonça Júnior 2013, Santana & Isaias 2014SANTANA AP & ISAIAS RMS. 2014. Galling insects are bioindicators of environmental quality in a Conservation Unit. Acta Bot Bras 28: 594-608., Nogueira et al. 2016NOGUEIRA, RM, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2016. Insect galls from Serra Geral, Caetité, BA, Brazil. Biota Neotrop 16: e20150035., Silva et al. 2018SILVA AF, NOGUEIRA RM, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2018. Occurrence and characterization of entomogenic galls in an area of Cerrado sensu stricto and Gallery forest of the state of Bahia, Brazil. An Acad Bras Cienc 90: 2903-2919.). Leaves are considered to be more plastic host organs as compared to stems (Isaias et al. 2013ISAIAS RMS, CARNEIRO RGS, OLIVEIRA DC & SANTOS JC. 2013. Illustrated and Annotated Checklist of Brazilian Gall Morphotypes. Neotrop Entomol 42: 230-239.). Additionally, it has been proposed that greater incidence of leaf galls reflects higher levels of nutritional reserves available in the leaves and their photosynthetic capacities (Castro et al. 2012CASTRO AC, OLIVEIRA DC, MOREIRA ASFP, LEMOS-FILHO JP & ISAIAS RMS. 2012. Source-sink relationship and photosynthesis in the horn-shaped gall and its host plant Copaifera langsdorffii Desf. (Fabaceae). S Afr J Bot 83: 121-126.). Almost all galls occurred on a single plant organ, confirming the gall-inducer specificity for the host plant organ (Dreger-Jauffret & Shorthouse 1992DREGER-JAUFFRET F & SHORTHOUSE JD. 1992. Diversity of gall-inducing insects and their galls. In: Shorthouse JD & Rohfritsch O (Eds), Biology of Insect-Induced Galls. Oxford University Press, Oxford, England, p. 285.).

Globoid, lenticular, and fusiform galls are generally the predominate shapes in inventories in the Neotropical region (e.g., Urso-Guimarães et al. 2003URSO-GUIMARÃES MVC, SCARELI-SANTOS C & BONIFÁCIO-SILVA A. 2003. Occurrence and characterization of entomogen galls in plants from natural vegetation areas in Delfinópolis, MG, Brazil. Braz J Biol 63: 705-715., Maia 2013aMAIA VC. 2013a. Insect galls from restingas of Southeastern Brazil, with new records. Biota Neotrop 13: 183-209., bMAIA VC. 2013b. Insect galls of São Tomé das Letras (MG, Brazil). Biota Neotrop 13: 164-189., Costa et al. 2014b, Vieira et al. 2018VIEIRA LG, NOGUEIRA RM, COSTA EC, CARVALHO- FERNANDES SP & SANTOS-SILVA J. 2018. Insect galls in rupestrian field and cerrado stricto sensu vegetation in Caetité, Bahia, Brasil. Biota Neotrop 18: e20170402., Silva et al. 2018SILVA AF, NOGUEIRA RM, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2018. Occurrence and characterization of entomogenic galls in an area of Cerrado sensu stricto and Gallery forest of the state of Bahia, Brazil. An Acad Bras Cienc 90: 2903-2919.). The association between gall morphotypes and host organs was observed, with most globoid and lenticular galls being found on leaves, while fusiform shapes were most common on host stems. Stem galls are often elongated and/or appressed to that organ, following length (Isaias et al. 2013ISAIAS RMS, CARNEIRO RGS, OLIVEIRA DC & SANTOS JC. 2013. Illustrated and Annotated Checklist of Brazilian Gall Morphotypes. Neotrop Entomol 42: 230-239., Ferreira & Isaias 2013FERREIRA BG & ISAIAS RMS. 2013. Developmental stem anatomy and tissue redifferentiation induced by a galling Lepidoptera on Marcetia taxifolia (Melastomataceae). Botany 91: 752-760., Santana & Isaias 2014SANTANA AP & ISAIAS RMS. 2014. Galling insects are bioindicators of environmental quality in a Conservation Unit. Acta Bot Bras 28: 594-608.). While leaf galls tend to distributed equally over the leaf blade, making maximum and efficient use of that surface as well as its total volume, which the cell expansions can occur in all directions (Isaias et al. 2013ISAIAS RMS, CARNEIRO RGS, OLIVEIRA DC & SANTOS JC. 2013. Illustrated and Annotated Checklist of Brazilian Gall Morphotypes. Neotrop Entomol 42: 230-239.).

The gall color were predominantly brown, similar to the colors reported in Cerrado and Caatinga-Cerrado transition sites in the Serra Geral at Caetité (Nogueira et al. 2016NOGUEIRA, RM, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2016. Insect galls from Serra Geral, Caetité, BA, Brazil. Biota Neotrop 16: e20150035.). The brown color of leaf galls often indicates their final stages of development (Carneiro et al. 2017CARNEIRO RG, ISAIAS R, MOREIRA AS & OLIVEIRA DC. 2017. Reacquisition of new meristematic sites determines the development of a new organ, the Cecidomyiidae gall on Copaifera langsdorffii Desf. (Fabaceae). Front Plant Sci 8: 1622.). In addition, the gall color can also indicate the presence of parasitoids or aposematism (Inbar et al. 2010INBAR M, IZHAKI I, KOPLOVICH A, LUPO, I, SILANIKOVE N, GLASSER T GERCHMAN Y, PEREVOLOTSKY A & LEV-YADUN S. 2010. Why do many galls have conspicuous colors? A new hipothesis. Arth Plant Int 4: 1-6., Dias et al. 2013DIAS GG, MOREIRA GRP, FERREIRA BG & ISAIAS RMS. 2013. Why do the galls induced by Calophya duvauae Scott on Schinus polygamus (Cav.) Cabrera (Anacardiaceae) change colors? Biochem Syst Ecol 48: 111-122.). As such, gall color variations represent an open field for research, and their colors may serve to alert predators to the possible presence of toxic compounds (Inbar et al. 2010INBAR M, IZHAKI I, KOPLOVICH A, LUPO, I, SILANIKOVE N, GLASSER T GERCHMAN Y, PEREVOLOTSKY A & LEV-YADUN S. 2010. Why do many galls have conspicuous colors? A new hipothesis. Arth Plant Int 4: 1-6.).

In spite of numerous inventories of galls in different Brazilian ecosystems, our lack of knowledge about the inducer insect species is a barrier to more comprehensive studies (Melo-Júnior et al. 2018MELO-JÚNIOR JCF, ISAIAS RMS, BOEGER MRT, ARRIOLA IA & MATILDE-SILVA M. 2018. Diversidade de galhadores nas restingas do ecossistema Babitonga, Santa Catarina, Brasil. Revista Cepsul - Biodiversidade e Conservação Marinha 7: eb2018003.). That situation reflects the difficulty of obtaining specimens of galling insects (including immature and adult phases of both sexes, necessary for species determinations), the prevalence of galls that have already been abandoned by their inducer, our general lack of knowledge of the life histories of the gall inducers, the limited number of taxonomists specialized in gall-inducing groups, and the high mortality rates to the host galler larvae, due the incidence of parasitoids (Espírito-Santo & Fernandes 2007ESPÍRITO-SANTO MM & FERNANDES GW. 2007. How Many Species of Gall-inducing insects are there on earth, and where are they? Ann Entomol Soc Am 100: 95-99., Carneiro et al. 2009bCARNEIRO MAA, BRANCO, CSA, BRAGA CED, ALMADA ED, COSTA MBM, MAIA, VC & FERNANDES GW. 2009b. Are gall midge species (Diptera, Cecidomyiidae) host-plant specialists? R Bras Entomol 53: 65-378., Gagné & Jaschhof 2017GAGNÉ RJ & JASCHHOF M. 2017. A Catalog of the Cecidomyiidae (Diptera) of the world. 4th ed., 762 p. https://www.ars.usda.gov/ARSUserFiles/80420580/Gagne_2017_World_Cat_4th_ed.pdf (Accessed September 2, 2020).
https://www.ars.usda.gov/ARSUserFiles/80...
, Melo-Júnior et al. 2018MELO-JÚNIOR JCF, ISAIAS RMS, BOEGER MRT, ARRIOLA IA & MATILDE-SILVA M. 2018. Diversidade de galhadores nas restingas do ecossistema Babitonga, Santa Catarina, Brasil. Revista Cepsul - Biodiversidade e Conservação Marinha 7: eb2018003.). Of the 98 gall morphotypes recorded in the present work, the insect inducers were identified in only 26 (24 insects to family, one to genus, and just one to species level [Myrciaryiamia admirabilis Maia, 2007, Diptera, Cecidomyiidae]). The Cecidomyiidae (Diptera) were found to be the principal gall inducers, as expected. Cecidomyiidae stands out in the literature as one of the principal gall-inducing groups in the Neotropics (e.g., Carneiro et al. 2009bCARNEIRO MAA, BRANCO, CSA, BRAGA CED, ALMADA ED, COSTA MBM, MAIA, VC & FERNANDES GW. 2009b. Are gall midge species (Diptera, Cecidomyiidae) host-plant specialists? R Bras Entomol 53: 65-378., Santos et al. 2011aSANTOS JC, ALMEIDA-CORTEZ JS & FERNANDES GW. 2011a. Diversity of gall-inducing insects in the high altitude wetland forests in Pernambuco, Northeast Brasil. Braz J Biol 71: 47-56., 2012a, b, Maia 2013aMAIA VC. 2013a. Insect galls from restingas of Southeastern Brazil, with new records. Biota Neotrop 13: 183-209., b, Costa et al. 2014bCOSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2014b. Galhas de insetos em uma área de transição caatinga-cerrado no Nordeste do Brasil. Sitientibus Ser Ci Biol 14: 1-9., Nogueira et al. 2016NOGUEIRA, RM, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2016. Insect galls from Serra Geral, Caetité, BA, Brazil. Biota Neotrop 16: e20150035., Gagné & Jaschhof 2017GAGNÉ RJ & JASCHHOF M. 2017. A Catalog of the Cecidomyiidae (Diptera) of the world. 4th ed., 762 p. https://www.ars.usda.gov/ARSUserFiles/80420580/Gagne_2017_World_Cat_4th_ed.pdf (Accessed September 2, 2020).
https://www.ars.usda.gov/ARSUserFiles/80...
, Silva et al. 2018SILVA AF, NOGUEIRA RM, COSTA EC, CARVALHO-FERNANDES SP & SANTOS-SILVA J. 2018. Occurrence and characterization of entomogenic galls in an area of Cerrado sensu stricto and Gallery forest of the state of Bahia, Brazil. An Acad Bras Cienc 90: 2903-2919., Santana et al. 2020SANTANA CAGS, COSTA EC, CARVALHO-FERNANDES S & SANTOS-SILVA J. 2020. Insect galls and their host plants in gallery forest in Bahia State, Brazil. Braz J Bot 43: 989-998., Santos-Silva & Araújo 2020SANTOS-SILVA J & ARAÚJO TJ 2020. Are Fabaceae the principal super- hosts of galls in Brazil? An Acad Bras Cienc 92: e20181115.).

The parasitoids were more frequent than inquilines, predators, and successors - another pattern recovered in our results. Plant galls are preyed upon by a diverse group of parasitoids belong to Hymenoptera. These organisms frequently cause high mortality rates to the host gall-inducing larvae (Weis & Abrahamson 1985WEIS AE & ABRAHAMSON WG. 1985. Potencial selective pressures by parasitoids on plant-herbivore interaction. Ecology 66: 1261-1269., Price & Clancy 1986PRICE PW & CLANCY KM. 1986. Interactions among three trophic levels: gall size and parasitoid attack. Ecology 67: 1593-1600.). The parasitoid community associated with host plant from Cerrado vegetation had already been widely reported in other inventories (Maia 2001MAIA VC. 2001. The gall midges (Diptera, Cecidomyiidae) from three restingas of Rio de Janeiro State, Brazil. Rev Bras Zool 18: 583-629., Maia & Fernandes 2004MAIA VC & FERNANDES GW. 2004. Insect galls from Serra de São José (Tiradentes, MG, Brazil). Braz J Biol 64: 423-445.).

Our results add evidences to the plant diversity hypothesis, the leaves as mainly host organ, the predominance of globoid gall, and Cecidomyiidae as one of the principal gall-inducing groups in Cerrado of Caetité, Bahia. We report new species of host plants and new gall morphotypes for the Brazilian Cerrado, which contribute to the understanding of the distribution and diversity of galls in the Cerrado. The great richness of gall morphotypes and host plants found and the high incidence of galling insects of uncertain taxonomic identities indicate that many of them must represent new records for the region, which suggests for the conservation of the two study areas. Additionally, the galling insect guild and the host plant composition varied among Cerrado localities, evidencing the importance of studying and preserving different areas of the same biomes.

ACKNOWLEDGMENTS

The authors are grateful to Msc. Jamile Jorge Ferreira, Cleiton Couto, and Jaqueline Teixeira for their help with the field collections; to Dr. Luciano Paganucci, Dr. Flávio França, and Dr. Efigênia de Mello at the Universidade Estadual de Feira de Santana (UEFS) for their help in identifying the botanical material; and to the Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq 406111/2016-2), the Fundação de Amparo à Pesquisa do Estado da Bahia (FAPESB 9648/2015) and the Universidade do Estado da Bahia (Propublic - 015/2019) for financial support. JSS is grateful to Fundação de Amparo à Pesquisa do Estado do Rio de Janeiro - FAPERJ (E-26/202.501/2019) and CNPq (160015/2019-7) for her research grant.

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Publication Dates

  • Publication in this collection
    24 Sept 2021
  • Date of issue
    2021

History

  • Received
    8 Sept 2020
  • Accepted
    16 Feb 2021
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