Literature DB >> 29674939

Dataset of long-term monitoring of ground-dwelling ants (Hymenoptera: Formicidae) in the influence areas of a hydroelectric power plant on the Madeira River in the Amazon Basin.

Itanna O Fernandes1, Jorge L P de Souza1,2.   

Abstract

BACKGROUND: Biodiversity loss is accelerating rapidly in response to increasing human influence on the Earth's natural ecosystems. One way to overcome this problem is by focusing on places of human interest and monitoring the changes and impacts on the biodiversity. This study was conducted at six sites within the influence area of the Santo Antônio Hydroelectric Power Plant in the margins of the Madeira River in Rondônia State. The sites cover a latitudinal gradient of approximately 100 km in the Brazilian Amazon Basin. The sampling design included six sampling modules with six plots (transects) each, totaling 30 sampling plots. The transects were distributed with 0 km, 0.5 km, 1 km, 2 km, 3 km and 4 km, measured perpendicularly from the river margin towards the interior of the forest. For sampling the ground-dwelling ants, the study used the ALL (ants of the leaf litter) protocol, which is standardized globally in the inventories of ant fauna. For the purpose of impact indicators, the first two campaigns (September 2011 to November 2011) were carried out in the pre-filling period, while campaigns 3 to 10 (February 2012 to November 2014) were carried out during and after the filling of the hydroelectric reservoir. A total of 253 events with a total of 9,165 occurrences were accounted during the monitoring. The ants were distributed in 10 subfamilies, 68 genera and 324 species/morphospecies. The impact on ant biodiversity during the periods before and after filling was measured by ecological indicators and by the presence and absence of some species/morphospecies. This is the first study, as far as we know, including taxonomic and ecological treatment to monitor the impact of a hydroelectric power plant on ant fauna. NEW INFORMATION: Until recently, most studies conducted on hydroelectric plants, located in the Amazon Basin, were carried out after the implementation of dams in order to assess their impacts on the environment and biodiversity (Benchimol and Peres 2015, Latrubesse et al. 2017, Sá-Oliveira et al. 2015). Recent studies on dam impacts have begun to be conducted prior to dam implementation (e.g. Bobrowiec and Tavares 2017, Fraga et al. 2014, Moser et al. 2014), thus providing a better overview of the impact and a better assessment of its magnitude.

Entities:  

Keywords:  Formicidae ; biodiversity; species occurrence; standardized sampling protocol; tropical forest.

Year:  2018        PMID: 29674939      PMCID: PMC5904506          DOI: 10.3897/BDJ.6.e24375

Source DB:  PubMed          Journal:  Biodivers Data J        ISSN: 1314-2828


Introduction

Biodiversity loss is accelerating rapidly in response to increasing human influence on the Earth’s natural ecosystems (Pimm et al. 1995, Vitousek 1997). Knowing the spatial and temporal organization of species in natural environments is essential for the understanding and conservation of biodiversity (Barton et al. 2013), as well as fostering land management decisions (Evans and Viengkham 2001). Large-scale, spatially structured sampling is a powerful tool to help land managers decide where to pursue conservation action most effectively (Turner et al. 1995). Even today, it is difficult to access accurate information on the spatial distribution of most organisms and their relationships with environmental variables at large scales, despite the availability of many methods for biodiversity planning and conservation (Barlow et al. 2010, Gibson et al. 2011, Margules et al. 2002). There are databases on species richness (Costello et al. 2013), but richness alone has limited use for conservation, because it does not give information on many endemic species or the complementarity of species compositions between regions (Groc et al. 2014, Lamoreux et al. 2005, Sarkar and Margules 2002). Furthermore, most assessments of species–habitat relationships can be compromised if the sampling design of surveys is not spatially clear (Gotelli et al. 2011). Invertebrate populations can indicate longer-term general ecosystem change, such as restoration of mine sites or climate change (e.g., McGeoch 1998, Bisevac and Majer 1999, Parmesan et al. 1999, York 2000). However, despite recognition that monitoring invertebrates is an important endeavour, widely accepted by national and international funding agencies, monitoring efforts have rarely generated returns commensurate to their investment. All too frequently, insect monitoring lacks both specific goals and a framework detailing how results will be integrated into management decision-making. One way to overcome these situations is by using good bioindicators taxa, as well as ants, considered particularly useful for monitoring for a number of reasons. Ants are one of the most successful groups of organisms on the planet (Hölldobler and Wilson 1990). To date, approximately 13,360 species of ants (antcat.org), all eusocial, have been described and hundreds of new species are described each year. Ant biologists estimate that the family could include no fewer than 20,000 species (Hölldobler and Wilson 1990). All species of ants occupy a nest structure, either temporarily or permanently. These structures can be preexisting cavities or even made their own bodies (e.g. army ants) that do not involve much, if any, excavation or direct modification of the surrounding environments (Guénard 2013). They are abundant and ubiquitous in both intact habitat and disturbed areas (Andersen 1990 Majer 1983, Hoffmann et al. 2000), sampling is relatively easy without requiring enormous expertise (Greenslade and Greenslade 1984, Fisher 1999, Agosti and Alonso 2000, Alonso 2000), and ants have proven sensitive and rapid responders to environmental variables (Campbell and Tanton 1981, Majer 1983 Andersen 1990). Moreover, ants are important functionally at many different trophic levels (Alonso 2000), and they play critical ecological roles in soil turnover and structure (Humphreys 1981, Lobry de Bruyn and Conacher 1994), nutrient cycling (Levieux 1983, Lal 1988), plant protection, seed dispersal, and seed predation (Ashton 1979, Beattie 1985, Christian 2001). Together, these qualities suggest ants merit monitoring for their own sake, as they provide high information content about an ecologically and numerically dominant group (Underwood and Fisher 2006). Despite the increased availability of methods for conservation planning, adequate information about the spatial distribution of biodiversity in large regions, such as the Amazon Basin, remains sparse for most biological groups (Margules et al. 2002). More than a hundred hydropower dams have already been built in the Amazon Basin and numerous proposals for further dam constructions are under consideration (Latrubesse et al. 2017). Recent scientific reviews have considered the environmental impacts of damming Amazonian rivers (Davidson et al. 2012, Castello and Macedo 2015, Winemiller et al. 2016, Fearnside 2016). The accumulated negative environmental effects of existing dams, not to mention proposed dams (if constructed), have triggered massive hydrophysical and biotic disturbances affecting the Amazon Basin’s floodplains, estuaries and sediment plumes (Latrubesse et al. 2017), as well as causing losses in river connectivity (Anderson et al. 2018). The Santo Antônio Hydroelectric Power Plant became operational at the beginning of 2016 in the Madeira River in Rondônia State. Prior to the construction of the Santo Antônio Plant, the fauna and flora of the impacted area were surveyed in environmental impact studies commissioned by the Brazilian Institute of Environment (IBAMA). The Santo Antônio Hydroelectric Power Plant and its accompanying reservoir represent the first time in history, as far as we know, in which a monitoring program of invertebrates was conducted to evaluate the influence before and after the total filling of the dam in the Amazon Basin.

Project description

Title

Environmental monitoring of ants (: ) in the influence areas of the Santo Antônio Hydroelectric Power Plant in the Madeira River in the Brazilian Amazon

Personnel

Itanna Oliveira Fernandes, Jorge Luiz Pereira de Souza

Study area description

The study was conducted at six sites associated with the Brazilian Biodiversity Research Program (PPBio) — Pedras, Búfalos, Morrinhos, Jaci-Paraná MD, Jaci-Paraná ME and Teotônio modules — within the influence area of the Santo Antônio Hydroelectric Power Plant in the margins of the Madeira River in Rondônia State.

Design description

Ants were sampled in permanent plots with five samples per sampling method. We used the RAPELD sampling design, which is based on a system of trails and permanent plots where a diverse range of taxa can be sampled (Costa and Magnusson 2010, Magnusson et al. 2005, Magnusson et al. 2013). The permanent plots are 250 m long and positioned to follow terrain contours to minimize the effects of topographical variation within plots. In each module, transects have a 1 km distance from each other, following the same spatial design.

Sampling methods

Study extent

The sites cover a latitudinal gradient of approximately 100 km in the Brazilian Amazon Basin. The sampling design included six sampling modules with six transects (Pedras, Búfalos, Morrinhos, Jaci-Paraná MD, Jaci-Paraná ME and Teotônio modules), each totalling 30 sampling plots. The transects were distributed 0 km, 0.5 km, 1 km, 2 km, 3 km and 4 km from the river's edge, measured perpendicularly from the river margin towards the interior of the forest. For the purpose of impact indicators, the first two campaigns (September 2011 to November 2011) were carried out in the pre-filling period, while campaigns 3 to 10 (February 2012 to November 2014) were carried out after the filling of the hydroelectric reservoir. The campaigns were conducted during the dry and rainy seasons of the Amazon over four years, with intervals of three months between each campaign (whenever possible).

Sampling description

Ants were sampled in permanent plots with five samples per sampling method along the transects 0 km, 0.5 km, 1 km, 2 km, 3 km and 4 km (Fig. 1). We used the RAPELD sampling design, which is based on a system of trails and permanent plots where a diverse range of taxa can be sampled (Costa and Magnusson 2010, Magnusson et al. 2005, Magnusson et al. 2013). The permanent plots are 250 m long and positioned to follow terrain contours to minimize the effects of topographical variation within plots. In each site, plots were 1 km apart from each other, following the same spatial design.
Figure 1.

Transects of each module to collect ants in the influence areas of the Santo Antônio Hydroelectric Power Plant, Porto Velho - RO, with perpendicular distances from the river margin. In details are each transect with a 1 km distance from each other following the same spatial design and each sampling plot in the permanent plots of 250 m length.

The protocol adopted for collection of litter ants is called the ALL protocol (leaflet ants), which is globally standardized on inventories of a litter of ant fauna (Agosti and Alonso 2000). Ground-dwelling ants collected in plots using litter samples were processed in Winkler extractors. Litter-dwelling ants were sampled from a 1 m2 litter in sampling plots located at 50 m intervals along the center line of each transect. Using a Winkler extractor with a 1 cm2 mesh sieve, the leaves were sifted through a wire sieve of 1 cm2 mesh size by shaking the sifter vigorously at least 15 times. The ants were extracted from the sifted litter and placed in a mesh bag inside a cotton bag for 24 hours (Fig. 2). If the sifted leaf litter volume exceeded the capacity of a single mini-Winkler extractor, a second extractor was used. In behavioural response to litter drying, the ants migrate from the suspended sample and fall into a container partially filled with alcohol at the bottom of the bag (Agosti et al. 2000, Bestelmeyer et al. 2000) (Fig. 3). The litter-sampling procedures were undertaken between 8:00 am and 5:00 pm. All ants were first identified to genus using the taxonomic keys provided by Baccaro et al. 2015. Then, they were sorted into species and morphospecies. We used available taxonomic keys or compared with specimens in collections previously identified by experts. A unique identification was given for each morphospecies based on morphological differences from related species. The morphotyping was the same for all collection sites. Vouchers are deposited in the invertebrate collection of the National Institute of Amazonian Research (INPA).
Figure 2.

Sample from 1 m2 leaf litter of each sampling plot located at 50 m intervals along the transect and mesh sieve used to separate the leaves from the invertebrates.

Figure 3.

Mini-Winkler extractors composed by a mesh bag filled with sifted sample inside and a cotton bag outside. In response to the drying, the ants migrate from the suspended sample and fall into a container partially filled with alcohol at the bottom of the bag.

Geographic coverage

Description

Areas of Santo Antônio Hydroelectric Power-Plant in Rondônia, Brazil.

Coordinates

-9.25 and -8.59 Latitude; -64.45 and -63.88 Longitude.

Taxonomic coverage

The ants were identified by species and morphospecies, as well as subfamily. Some genera were recorded for the first time in South America ( Roger, 1861) and others in Rondônia State ( Emery, 1906; Brown & Kempf, 1961; Wheeler, 1910; Emery, 1913; Emery, 1913; Wheeler, 1910; and Mayr, 1870). We also obtained new records of the following species for Rondônia State: , , , , , , , , , , , , , , , and . A total of 46,342 individuals were collected during four years of field collections. A list of all the ants identified in subfamilies (10), genera (68) and species/morphospecies (324). More information about the ecological data and occurence is available in Suppl. materials 1, 2

Traits coverage

Data coverage of traits

PLEASE FILL IN TRAIT INFORMATION HERE

Temporal coverage

Notes

2011-09-02 through 2011-09-09, 2011-11-17 through 2012-12-03, 2012-02-28 through 2012-03-12, 2012-05-30 through 2012-06-11, 2013-09-19 through 2013-01-31, 2013-04-18 through 2013-04-28, 2013-06-28 through 2013-07-05, 2013-10-20 through 2013-09-26, 2014-01-17 through 2014-01-27, 2014-11-13 through 2014-11-23

Collection data

Collection name

Instituto Nacional de Pesquisas da Amazônia - INPA/ Coleção de Invertebrados/ HYM

Specimen preservation method

alcohol, pinned

Usage rights

Use license

Other

IP rights notes

This work is licensed under a Creative Commons Attribution Non Commercial (CC-BY-NC) 4.0 License.

Data resources

Data package title

Environmental monitoring of ants (: ) in the influence areas of Santo Antônio Hydroelectric Power-Plant in Rondônia, Brazil.

Alternative identifiers

914c3b86-f2a1-4d5e-b343-b2597b9d4542, https://ipt.sibbr.gov.br/sibbr/resource?r=ant_monitoring_in_santo_antonio_hydroelectric_power_plant_rondonia

Number of data sets

2

Data set 1.

Data set name

Environmental monitoring of ants (: ) in the influence areas of Santo Antônio Hydroelectric Power-Plant in Rondônia, Brazil.

Data format

Darwin Core

Number of columns

26

Character set

Event

Description

Biodiversity loss is accelerating rapidly in response to increasing human influence on the Earth’s natural ecosystems. One way to overcome this problem is by focusing on places of human interest and monitoring the changes and impacts on the biodiversity. This study was conducted at six sites within the influence area of the Santo Antônio Hydroelectric Power Plant in the margins of the Madeira River, Rondônia. The sites cover a latitudinal gradient of approximately 100 km in the Brazilian Amazon Basin. The sampling design included six sampling modules with six transects in each module, totaling 30 sampling plots in each module. Transects were distrubuted with 0 km, 0.5 km, 1 km, 2 km, 3 km, and 4 km, measured perpendicularly from the river margin towards the interior of the forest. For sampling the ground-dwelling ants, we used the ALL (ants of the leaf litter) protocol, which is standardized globally in the inventories of ant fauna. For the purpose of impact indicators, the first two campaigns (September 2011 to November 2011) were carried out in the pre-filling period, while campaigns 3 to 10 (Febuary 2012 to November 2014) were carried out during and after the filling of the hydroelectric reservoir. A total of 253 events with a total of 9.165 occurrences were accounted during the monitoring. The ants were distributed in 10 subfamilies, 68 genera, and 324 species/morphospecies (Fig. 4). The impact on ant biodiversity during the periods before and after filling was measured by ecological indicators and by the presence and absence of some species/morphospecies. This is the first study, as far as we know, including taxonomic and ecological treatment to monitor the impact of a hydroelectric power plant on ant fauna.
Figure 4.

Species occurrence before and after reservoir filling in the Santo Antônio Hydroelectric Power Plant. Dotted lines mark the 95% confidence intervals.

Data set 2.

Environmental monitoring of ants (: ) in the influence areas of Santo Antônio Hydroelectric Power-Plant in Rondônia, Brazil. 33 Occurrence

Additional information

Fernandes I (2017): Environmental monitoring of ants (: ) in the influence areas of Santo Antônio Hydroelectric Power-Plant in Rondônia, Brazil. v1.7. Sistema de Informação sobre a Biodiversidade Brasileira - SiBBr. Dataset/Samplingevent. https://ipt.sibbr.gov.br/sibbr/resource?r=ant_monitoring_in_santo_antonio_hydroelectric_power_plant_rondonia&v=1.7 A total of 253 events of collection in the influence areas of Santo Antônio Hydroelectric Power-Plant. Data type: metadata (DwC-A) event File: oo_182359.xlsx A total of 9.165 occurrences in the influence areas of Santo Antônio Hydroelectric Power-Plant. Data type: metadata (DwC-A) occurences File: oo_182361.xlsx
RankScientific NameCommon Name
familyFormicidae Latreille, 1809ant
subfamilyAgroecomyrmecinae Carpenter, 1930ant
genusTatuidris Brown & Kempf, 1968ant
speciesTatuidris tatusia Brown & Kempf, 1968ant
subfamilyAmblyoponinae Forel, 1893ant
genusFulakora Mann, 1919ant
speciesFulakora degenerata (Borgmeier, 1957)ant
genusPrionopelta Mayr, 1866ant
speciesPrionopelta sp. 1ant
subfamilyDolichoderinae Forel, 1878ant
genusAzteca Forel, 1878ant
speciesAzteca cf. chartiffex Emery, 1896ant
speciesAzteca sp. 1ant
speciesAzteca sp. 2ant
speciesAzteca sp. 3ant
speciesAzteca sp. 4ant
speciesAzteca sp. 5ant
genusDolichoderus Lund, 1831ant
speciesDolichoderus bidens (Linnaeus, 1758)ant
speciesDolichoderus bispinosus (Olivier, 1792)ant
speciesDolichoderus cogitans Forel, 1912ant
speciesDolichoderus debilis Emery, 1890ant
speciesDolichoderus decollatus Smith, 1858ant
speciesDolichoderus imitator Emery, 1894ant
speciesDolichoderus longicollis MacKay, 1993ant
speciesDolichoderus septemspinosus Emery, 1894ant
speciesDolichoderus sp. 1ant
genusLinepithema Mayr, 1866ant
speciesLinepithema sp. 1ant
genusTapinoma Foerster, 1850ant
speciesTapinoma melanocephalum (Fabricius, 1793)ant
speciesTapinoma sp. 1ant
subfamilyDorylinae Leach, 1815ant
genusCheliomyrmex Mayr, 1870ant
speciesCheliomyrmex megalonyx Wheeler, 1921ant
genusEciton Latreille, 1804ant
speciesEciton burchellii (Westwood, 1842)ant
genusLabidus Jurine, 1807ant
speciesLabidus praedator (Smith, 1858)ant
speciesLabidus spininodis (Emery, 1890)ant
genusNeivamyrmex Borgmeier, 1940ant
speciesNeivamyrmex adnepos (Wheeler, 1922)ant
speciesNeivamyrmex angustinodis (Emery, 1888)ant
speciesNeivamyrmex sp. 3ant
genusNeocerapachys Borowiec, 2016ant
speciesNeocerapachys splendens (Borgmeier, 1957)ant
genusSyscia Roger, 1861ant
speciesSyscia augustae (Wheeler, 1902)ant
subfamilyEctatomminae Emery, 1895ant
genusEctatomma Smith, 1858ant
speciesEctatomma brunneum Smith, 1858ant
speciesEctatomma edentatum Roger, 1863ant
speciesEctatomma lugens Emery, 1894ant
genusGnamptogenys Roger, 1863ant
speciesGnamptogenys acuminata (Emery, 1896)ant
speciesGnamptogenys caelata Kempf, 1967ant
speciesGnamptogenys ericae (Forel, 1912)ant
speciesGnamptogenys haenschi (Emery, 1902)ant
speciesGnamptogenys horni (Santschi, 1929)ant
speciesGnamptogenys kempfi Lenko, 1964ant
speciesGnamptogenys moelleri (Forel, 1912)ant
speciesGnamptogenys pleurodon (Emery, 1896)ant
speciesGnamptogenys relicta (Mann, 1916)ant
speciesGnamptogenys sp. 1ant
speciesGnamptogenys sp. 11ant
speciesGnamptogenys sp. 3ant
speciesGnamptogenys sp. 5ant
speciesGnamptogenys tortuolosa (Smith, 1858)ant
genusTyphlomyrmex Mayr, 1862ant
speciesTyphlomyrmex sp. 1ant
subfamilyFormicinae Latreille, 1809ant
genusAcropyga Roger, 1862ant
speciesAcropyga sp. 1ant
genusBrachymyrmex Mayr, 1868ant
speciesBrachymyrmex sp. 1ant
speciesBrachymyrmex sp. 2ant
speciesBrachymyrmex sp. 3ant
speciesBrachymyrmex sp. 4ant
speciesBrachymyrmex sp. 5ant
speciesBrachymyrmex sp. 6ant
genusCamponotus Mayr, 1861.ant
speciesCamponotus atriceps (Smith, 1858)ant
speciesCamponotus blandus (Smith, 1858)ant
speciesCamponotus cameranoi Emery, 1894ant
speciesCamponotus crassus Mayr, 1862ant
speciesCamponotus fastigatus Roger, 1863ant
speciesCamponotus femoratus (Fabricius, 1804)ant
speciesCamponotus novogranadensis Mayr, 1870ant
speciesCamponotus rapax (Fabricius, 1804)ant
speciesCamponotus rectangularis Emery, 1890ant
speciesCamponotus sericeiventris (Guérin-Méneville, 1838)ant
speciesCamponotus sp. 5ant
speciesCamponotus sp. 6ant
genusGigantiops Roger, 1863ant
speciesGigantiops destructor (Fabricius, 1804)ant
genusNylanderia Emery, 1906ant
speciesNylanderia cf. caeciliae (Forel, 1899)ant
speciesNylanderia cf. fulva (Mayr, 1862)ant
speciesNylanderia cf. guatemalensis (Forel, 1885)ant
speciesNylanderia sp. 3ant
speciesNylanderia sp. 5ant
subfamilyMyrmicinae Lepeletier de Saint-Fargeau, 1835ant
genusAcromyrmex Mayr, 1865ant
speciesAcromyrmex cf. subterraneus (Forel, 1893)ant
genusAllomerus Mayr, 1878ant
speciesAllomerus octoarticulatus Mayr, 1878ant
genusApterostigma Mayr, 1865ant
speciesApterostigma auriculatum Wheeler, 1925ant
species Apterostigma gr. pilosum ant
genusAtta Fabricius, 1804ant
speciesAtta cephalotes (Linnaeus, 1758)ant
speciesAtta sexdens (Linnaeus, 1758)ant
genusBasiceros Schulz, 1906ant
speciesBasiceros militaris (Weber, 1950)ant
genusBlepharidatta Wheeler, 1915ant
speciesBlepharidatta brasiliensis Wheeler, 1915ant
genusCarebara Westwood, 1840ant
species Carebara gr. lignata ant
speciesCarebara sp. 1ant
speciesCarebara sp. 2ant
speciesCarebara sp. 5ant
speciesCarebara urichi (Wheeler, 1922)ant
genusCephalotes Latreille, 1802ant
speciesCephalotes atratus (Linnaeus, 1758)ant
speciesCephalotes minutus (Fabricius, 1804)ant
speciesCephalotes pellans De Andrade, 1999ant
speciesCephalotes pusillus (Klug, 1824)ant
speciesCephalotes sp. 1ant
speciesCephalotes sp. 2ant
speciesCephalotes sp. 3ant
genusCrematogaster Lund, 1831ant
speciesCrematogaster acuta (Fabricius, 1804)ant
speciesCrematogaster brasiliensis Mayr, 1878ant
speciesCrematogaster carinata Mayr, 1862ant
speciesCrematogaster curvispinosa Mayr, 1862ant
speciesCrematogaster flavosensitiva Longino, 2003ant
speciesCrematogaster limata Smith, 1858ant
speciesCrematogaster longispina Emery, 1890ant
speciesCrematogaster nigropilosa Mayr, 1870ant
speciesCrematogaster sotobosque Longino, 2003ant
speciesCrematogaster sp. 2ant
speciesCrematogaster stollii Forel, 1885ant
speciesCrematogaster tenuicula Forel, 1904ant
genusCyphomyrmex Mayr, 1862ant
speciesCyphomyrmex laevigatus Weber, 1938ant
speciesCyphomyrmex minutus Mayr, 1862ant
speciesCyphomyrmex peltatus Kempf, 1966ant
speciesCyphomyrmex rimosus (Spinola, 1851)ant
speciesCyphomyrmex cf. salvini Forel, 1899ant
speciesCyphomyrmex sp. 12ant
speciesCyphomyrmex sp. 13ant
speciesCyphomyrmex sp. 3ant
speciesCyphomyrmex sp. 4ant
genusEurhopalothrix Brown & Kempf, 1961ant
speciesEurhopalothrix pilulifera Brown & Kempf, 1960ant
genusHylomyrma Forel, 1912ant
speciesHylomyrma dentiloba (Santschi, 1931)ant
speciesHylomyrma cf. dolichops Kempf, 1973ant
speciesHylomyrma immanis Kempf, 1973ant
speciesHylomyrma longiscapa Kempf, 1961ant
speciesHylomyrma cf. reitteri (Mayr, 1887)ant
speciesHylomyrma sp. 2ant
speciesHylomyrma sp. 3ant
genusLachnomyrmex Wheeler, 1910ant
speciesLachnomyrmex sp. 1ant
genusMegalomyrmex Forel, 1885ant
speciesMegalomyrmex balzani Emery, 1894ant
speciesMegalomyrmex cuatiara Brandão, 1990ant
speciesMegalomyrmex drifti Kempf, 1961ant
speciesMegalomyrmex goeldii Forel, 1912ant
speciesMegalomyrmex leoninus Forel, 1885ant
speciesMegalomyrmex sp. 2ant
speciesMegalomyrmex sp. 5ant
speciesMegalomyrmex sp. 8ant
speciesMegalomyrmex wallacei Mann, 1916ant
genusMonomorium Mayr, 1855ant
speciesMonomorium pharaonis (Linnaeus, 1758)ant
genusMycetarotes Emery, 1913ant
speciesMycetarotes sp. 1ant
genusMycetophylax Emery, 1913ant
speciesMycetophylax cf. lectus (Forel, 1911)ant
speciesMycetophylax strigatus (Mayr, 1887)ant
genusMycocepurus Forel, 1893ant
speciesMycocepurus goeldii (Forel, 1893)ant
speciesMycocepurus sp. 1ant
speciesMycocepurus sp. 2ant
speciesMycocepurus sp. 3ant
genusMyrmicocrypta Smith, 1860ant
speciesMyrmicocrypta sp. 1ant
speciesMyrmicocrypta sp. 2ant
genusNesomyrmex Wheeler, 1910ant
speciesNesomyrmex pleuriticus (Kempf, 1959)ant
genusOchetomyrmex Mayr, 1878ant
speciesOchetomyrmex semipolitus Mayr, 1878ant
genusOctostruma Forel, 1912ant
speciesOctostruma balzani (Emery, 1894)ant
speciesOctostruma iheringi (Emery, 1888)ant
speciesOctostruma sp. 1ant
speciesOctostruma sp. 2ant
speciesOctostruma sp. 3ant
genusOxyepoecus Santschi, 1926ant
speciesOxyepoecus ephippiatus Albuquerque & Brandão, 2004ant
genusPheidole Westwood, 1839ant
speciesPheidole fracticeps Wilson, 2003ant
speciesPheidole biconstricta Mayr, 1870ant
speciesPheidole flavens Roger, 1863ant
speciesPheidole vorax (Fabricius, 1804)ant
speciesPheidole sp. 1ant
speciesPheidole sp. 4ant
speciesPheidole sp. 6ant
speciesPheidole sp. 4ant
speciesPheidole sp. 6ant
speciesPheidole sp. 10ant
speciesPheidole sp. 11ant
speciesPheidole sp. 12ant
speciesPheidole sp. 14ant
speciesPheidole sp. 15ant
speciesPheidole sp. 16ant
speciesPheidole sp. 17ant
speciesPheidole sp. 18ant
speciesPheidole sp. 19ant
speciesPheidole sp. 2ant
speciesPheidole sp. 20ant
speciesPheidole sp. 21ant
speciesPheidole sp. 22ant
speciesPheidole sp. 23ant
speciesPheidole sp. 24ant
speciesPheidole sp. 26ant
speciesPheidole sp. 27ant
speciesPheidole sp. 28ant
speciesPheidole sp. 29ant
speciesPheidole sp. 3ant
speciesPheidole sp. 30ant
speciesPheidole sp. 32ant
speciesPheidole sp. 40ant
speciesPheidole sp. 41ant
speciesPheidole sp. 42ant
speciesPheidole sp. 43ant
speciesPheidole sp. 44ant
speciesPheidole sp. 45ant
speciesPheidole sp. 46ant
speciesPheidole sp. 47ant
speciesPheidole sp. 48ant
speciesPheidole sp. 49ant
speciesPheidole sp. 5ant
speciesPheidole sp. 50ant
speciesPheidole sp. 51ant
speciesPheidole sp. 52ant
speciesPheidole sp. 53ant
speciesPheidole sp. 54ant
speciesPheidole sp. 55ant
speciesPheidole sp. 7ant
speciesPheidole sp. 8ant
speciesPheidole sp. 9ant
genusRhopalothrix Mayr, 1870ant
speciesRhopalothrix sp. 1ant
speciesRhopalothrix sp. 2ant
genusRogeria Emery, 1894ant
speciesRogeria alzatei Kugler, 1994ant
speciesRogeria cf. belti Mann, 1922ant
speciesRogeria blanda (Smith, 1858)ant
speciesRogeria cf. cornuta Kugler, 1994ant
speciesRogeria cf. cuneola Kugler, 1994ant
speciesRogeria leptonana Kugler, 1994ant
speciesRogeria sp. 1ant
speciesRogeria sp. 2ant
genusSericomyrmex Mayr, 1865ant
speciesSericomyrmex sp. 1ant
speciesSericomyrmex sp. 2ant
genusSolenopsis Westwood, 1840ant
speciesSolenopsis cf. castor Forel, 1893ant
speciesSolenopsis cf. clytemnestra Emery, 1896ant
speciesSolenopsis geminata (Fabricius, 1804)ant
species Solenopsis gr. molesta ant
speciesSolenopsis cf. loretana Santschi, 1936ant
speciesSolenopsis cf. saevissima (Smith, 1855)ant
speciesSolenopsis sp. 3ant
speciesSolenopsis sp. 5ant
speciesSolenopsis sp. 7ant
speciesSolenopsis substituta Santschi, 1925ant
genusStegomyrmex Emery, 1912ant
speciesStegomyrmex cf. olindae Feitosa, Brandão & Diniz, 2008ant
genusStrumigenys Smith, 1860ant
speciesStrumigenys appretiata (Borgmeier, 1954)ant
speciesStrumigenys beebei (Wheeler, 1915)ant
speciesStrumigenys deinomastax (Bolton, 2000)ant
speciesStrumigenys denticulata Mayr, 1887ant
speciesStrumigenys elongata Roger, 1863ant
speciesStrumigenys infidelis Santschi, 1919ant
speciesStrumigenys inusitata (Lattke, 1992)ant
speciesStrumigenys cf. perparva Brown, 1958ant
speciesStrumigenys smithii Forel, 1886ant
speciesStrumigenys sp. 1ant
speciesStrumigenys sp. 10ant
speciesStrumigenys sp. 13ant
speciesStrumigenys sp. 14ant
speciesStrumigenys sp. 15ant
speciesStrumigenys sp. 2ant
speciesStrumigenys sp. 3ant
speciesStrumigenys sp. 4ant
speciesStrumigenys sp. 5ant
speciesStrumigenys sp. 6ant
speciesStrumigenys sp. 7ant
speciesStrumigenys sp. 8ant
speciesStrumigenys sp. 9ant
speciesStrumigenys cf. trinidadensis Wheeler, 1922ant
speciesStrumigenys trudifera Kempf & Brown, 1969ant
speciesStrumigenys zeteki (Brown, 1959)ant
genusTrachymyrmex Forel, 1893ant
speciesTrachymyrmex cf. bugnioni (Forel, 1912)ant
speciesTrachymyrmex cf. cornetzi (Forel, 1912)ant
speciesTrachymyrmex cf. diversus Mann, 1916ant
speciesTrachymyrmex cf. farinosus (Emery, 1894)ant
speciesTrachymyrmex cf. mandibularis Weber, 1938ant
speciesTrachymyrmex cf. opulentus (Mann, 1922)ant
speciesTrachymyrmex cf. ruthae Weber, 1937ant
speciesTrachymyrmex sp. 10ant
speciesTrachymyrmex sp. 3ant
speciesTrachymyrmex sp. 7ant
speciesTrachymyrmex sp. 8ant
speciesTrachymyrmex sp. 9ant
genusTranopelta Mayr, 1866ant
speciesTranopelta gilva Mayr, 1866ant
speciesTranopelta sp. 1ant
genusWasmannia Forel, 1893ant
speciesWasmannia auropunctata (Roger, 1863)ant
speciesWasmannia rochai Forel, 1912ant
speciesWasmannia scrobifera Kempf, 1961ant
speciesWasmannia sp. 1ant
subfamilyPonerinae Lepeletier de Saint-Fargeau, 1835ant
genusAnochetus Mayr, 1861ant
speciesAnochetus diegensis Forel, 1912ant
speciesAnochetus emarginatus (Fabricius, 1804)ant
speciesAnochetus horridus Kempf, 1964ant
speciesAnochetus mayri Emery, 1884ant
speciesAnochetus neglectus Emery, 1894ant
speciesAnochetus targionii Emery, 1894ant
genusDinoponera Roger, 1861ant
speciesDinoponera gigantea (Perty, 1833)ant
genusHypoponera Santschi, 1938ant
speciesHypoponera sp. 1ant
speciesHypoponera sp. 16ant
speciesHypoponera sp. 2ant
speciesHypoponera sp. 3ant
speciesHypoponera sp. 4ant
speciesHypoponera sp. 5ant
speciesHypoponera sp. 6ant
speciesHypoponera sp. 7ant
speciesHypoponera sp. 8ant
speciesHypoponera sp. 9ant
genusLeptogenys Roger, 1861ant
speciesLeptogenys unistimulosa Roger, 1863ant
genusMayaponera Schmidt & Shattuck, 2014ant
speciesMayaponera constricta (Mayr, 1884)ant
genusNeoponera Emery, 1901ant
speciesNeoponera apicalis (Latreille, 1802)ant
speciesNeoponera cavinodis Mann, 1916ant
speciesNeoponera commutata (Roger, 1860)ant
speciesNeoponera laevigata (Smith, 1858)ant
speciesNeoponera unidentata (Mayr, 1862)ant
speciesNeoponera venusta Forel, 1912ant
speciesNeoponera verenae Forel, 1922ant
genusOdontomachus Latreille, 1804ant
speciesOdontomachus bauri Emery, 1892ant
speciesOdontomachus caelatus Brown, 1976ant
speciesOdontomachus chelifer (Latreille, 1802)ant
speciesOdontomachus haematodus (Linnaeus, 1758)ant
speciesOdontomachus hastatus (Fabricius, 1804)ant
speciesOdontomachus laticeps Roger, 1861ant
speciesOdontomachus meinerti Forel, 1905ant
speciesOdontomachus sp. 1ant
speciesOdontomachus sp. 2ant
genusPachycondyla Smith, 1858ant
speciesPachycondyla crassinoda (Latreille, 1802)ant
speciesPachycondyla harpax (Fabricius, 1804)ant
speciesPachycondyla impressa (Roger, 1861)ant
speciesPachycondyla sp. 1ant
speciesPachycondyla sp. 2ant
speciesPachycondyla sp. 3ant
speciesPachycondyla striata Smith, 1858ant
genusPseudoponera Emery, 1900ant
speciesPseudoponera stigma (Fabricius, 1804)ant
genusRasopone Schmidt & Shattuck, 2014ant
speciesRasopone arhuaca (Forel, 1901)ant
genusSimopelta Mann, 1922ant
speciesSimopelta anomma Fernandes et al., 2015ant
speciesSimopelta jeckylli (Mann, 1916)ant
genusThaumatomyrmex Mayr, 1887ant
speciesThaumatomyrmex atrox Weber, 1939ant
subfamilyProceratiinae Emery, 1895ant
genusDiscothyrea Roger, 1863ant
speciesDiscothyrea denticulata Weber, 1939ant
speciesDiscothyrea humilis Weber, 1939ant
speciesDiscothyrea sexarticulata Borgmeier, 1954ant
subfamilyPseudomyrmecinae Smith, 1952ant
genusPseudomyrmex Lund, 1831ant
speciesPseudomyrmex ita (Forel, 1906)ant
speciesPseudomyrmex simplex (Smith, 1877)ant
speciesPseudomyrmex sp. 2ant
speciesPseudomyrmex sp. 3ant
speciesPseudomyrmex tenuis (Fabricius, 1804)ant
speciesPseudomyrmex termitarius (Smith, 1855)ant
Data set 1.
Column labelColumn description
eventIDAn identifier for the set of information associated with an Event (something that occurs at a place and time).
eventDateThe date-time or interval during which an Event occurred. For occurrences, this is the date-time when the event was recorded.
eventTimeThe time or interval during which an Event occurred.
habitatA category or description of the habitat in which the Event occurred.
samplingProtocolThe name of, reference to, or description of the method or protocol used during an Event.
samplingEffortThe amount of effort expended during an Event.
eventRemarksComments or notes about the Event.
sampleSizeUnitThe unit of measurement of the size (time duration, length, area or volume) of a sample in a sampling event.
sampleSizeValueA numeric value for a measurement of the size (time duration, length, area or volume) of a sample in a sampling event.
fieldNotesThe text of notes taken in the field about the Event.
continentThe name of the continent in which the Location occurs.
countryThe name of the country or major administrative unit in which the Location occurs
countryCodeThe standard code for the country in which the Location occurs.
stateProvinceThe name of the next smaller administrative region than country (state, province, canton, department, region, etc.) in which the Location occurs.
countyThe full, unabbreviated name of the next smaller administrative region than stateProvince (county, shire, department, etc.) in which the Location occurs.
localityThe specific description of the place.
locationRemarksComments or notes about the Location.
decimalLongitudeThe geographic longitude (in decimal degrees, using the spatial reference system given in geodeticDatum) of the geographic center of a Location.
decimalLatitudeThe geographic latitude (in decimal degrees, using the spatial reference system given in geodeticDatum) of the geographic center of a Location.
modifiedThe most recent date-time on which the resource was changed.
datasetNameThe name identifying the data set from which the record was derived.
typeA list of nomenclatural types.
languageA language of the resource.
institutionIDAn identifier for the institution having custody of the material referred to in the record.
institutionCodeThe acronym in use by the institution having custody of the material referred to in the record.
rightsHolderThe organization owning the rights over the resource.
Data set 2.
Column labelColumn description
IDAn identifier for the Identification (an identifier specific to the data set).
typeA list of nomenclatural types.
modifiedThe most recent date-time on which the resource was changed.
languageA language of the resource.
licenseA legal document giving official permission to do something with the resource.
rightsHolderThe organization owning the material rights over the resource.
institutionIDAn identifier for the institution having custody of the material referred to in the record.
institutionCodeThe acronym in use by the institution having custody of the material referred to in the record.
datasetNameThe name identifying the data set from which the record was derived.
basisOfRecordThe specific nature of the data record.
dynamicPropertiesA list of additional measurements, facts, characteristics, or assertions about the record.
occurrenceIDAn identifier for the Occurrence.
recordNumberAn identifier given to the Occurrence at the time it was recorded.
recordedByA list of names of people responsible for recording the original Occurrence.
organismQuantityA number for the quantity of organisms.
organismQuantityTypeThe type of quantification system used for the quantity of organisms.
sexThe sex of the biological individual(s) represented in the Occurrence.
lifeStageThe age class or life stage of the biological individual(s) at the time the Occurrence was recorded.
reproductiveConditionThe reproductive condition of the biological individual(s) represented in the Occurrence.
preparationsA list of preparations and preservation methods for a specimen.
dispositionThe current state of a specimen with respect to the collection identified in collectionCode or collectionID.
eventIDAn identifier for the set of information associated with an Event (something that occurs at a place and time).
identifiedByA list of names of people who assigned the Taxon to the subject.
scientificNameAn identifier for the nomenclatural details of a scientific name.
kingdomThe full scientific name of the kingdom in which the taxon is classified.
phylumThe full scientific name of the phylum or division in which the taxon is classified.
classThe full scientific name of the class in which the taxon is classified.
orderThe full scientific name of the order in which the taxon is classified.
familyThe full scientific name of the family in which the taxon is classified.
genusThe full scientific name of the genus in which the taxon is classified.
specificEpithetThe name of the first or species epithet of the scientificName.
taxonRankThe taxonomic rank of the most specific name in the scientificName.
vernacularNameA common or vernacular name.
  17 in total

Review 1.  Operationalizing biodiversity for conservation planning.

Authors:  Sahotra Sarkar; Chris Margules
Journal:  J Biosci       Date:  2002-07       Impact factor: 1.826

Review 2.  Representing biodiversity: data and procedures for identifying priority areas for conservation.

Authors:  C R Margules; R L Pressey; P H Williams
Journal:  J Biosci       Date:  2002-07       Impact factor: 1.826

Review 3.  The Amazon basin in transition.

Authors:  Eric A Davidson; Alessandro C de Araújo; Paulo Artaxo; Jennifer K Balch; I Foster Brown; Mercedes M C Bustamante; Michael T Coe; Ruth S DeFries; Michael Keller; Marcos Longo; J William Munger; Wilfrid Schroeder; Britaldo S Soares-Filho; Carlos M Souza; Steven C Wofsy
Journal:  Nature       Date:  2012-01-18       Impact factor: 49.962

4.  Global tests of biodiversity concordance and the importance of endemism.

Authors:  John F Lamoreux; John C Morrison; Taylor H Ricketts; David M Olson; Eric Dinerstein; Meghan W McKnight; Herman H Shugart
Journal:  Nature       Date:  2005-12-28       Impact factor: 49.962

5.  Biodiversity data should be published, cited, and peer reviewed.

Authors:  Mark J Costello; William K Michener; Mark Gahegan; Zhi-Qiang Zhang; Philip E Bourne
Journal:  Trends Ecol Evol       Date:  2013-06-05       Impact factor: 17.712

6.  The future of biodiversity.

Authors:  S L Pimm; G J Russell; J L Gittleman; T M Brooks
Journal:  Science       Date:  1995-07-21       Impact factor: 47.728

7.  CONSERVATION. Brazilian politics threaten environmental policies.

Authors:  Philip M Fearnside
Journal:  Science       Date:  2016-08-19       Impact factor: 47.728

8.  Primary forests are irreplaceable for sustaining tropical biodiversity.

Authors:  Luke Gibson; Tien Ming Lee; Lian Pin Koh; Barry W Brook; Toby A Gardner; Jos Barlow; Carlos A Peres; Corey J A Bradshaw; William F Laurance; Thomas E Lovejoy; Navjot S Sodhi
Journal:  Nature       Date:  2011-09-14       Impact factor: 49.962

9.  Consequences of a biological invasion reveal the importance of mutualism for plant communities.

Authors:  C E Christian
Journal:  Nature       Date:  2001-10-11       Impact factor: 49.962

10.  Establishing baseline biodiversity data prior to hydroelectric dam construction to monitoring impacts to bats in the Brazilian Amazon.

Authors:  Paulo Estefano D Bobrowiec; Valéria da Cunha Tavares
Journal:  PLoS One       Date:  2017-09-08       Impact factor: 3.240

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