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Disturbance | Aim | Indication | Environmental parameters | Effects on ant community | Indicator type | Reference |
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Agriculture | Evaluate the effect of different soil tillage and crop management systems on soil fauna groups | Yes (implicit) | Soil tillage and crop management systems | Change in species dominance (discriminant and correspondence analysis) | Environmental | Baretta et al. [28] |
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Agriculture | Evaluate the ant diversity in fig crops under different managements | Yes | Types of soil cover plants | Change in density of species (, Tukey test) | Environmental | Merlim et al. [29] |
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Agriculture (forestry practices in Eucalyptus) | Use the ant guild concept to evaluate changes in Eucalyptus plantations following control of leaf-cutting ants | Yes | Forestry practices | Change in species composition—observed frequency of species and guilds (non-statistical test) | Environmental | Lacau et al. [30] |
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Agriculture (preceded by deforestation and fire) | Assess the recolonization by fauna in areas cleared and burned to plant corn and beans | Yes | Human land-use and resting time | Increase in abundance in the less-disturbed areas (non-statistical test) | Environmental | Nunes et al. [31] |
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Agriculture (formicid granulated baits) | Evaluate the effect of different applications of formicide baits on nontarget ant community | Yes | Forms and timing of application of formicid-granulated baits | No effect of bait type on ant species richness (, ANOVA) Reduction in species richness observed only in control method, systematic application being more harmful (, ANOVA) | Environmental | Ramos et al. [32] |
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Anthropogenic activities | Quantify heavy metals in worker ants of Camponotus rufipes collected in different environments | Yes | Observed human interference | Three groups of ants with different heavy metal concentrations (PCA analyses) | Environmental | Silva et al. [33] |
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Conservation status | Create an inventory of epigaeic ant species that occur in vine forest and use them to indicate the level of conservation of this ecosystem | Yes | None | Inventory (nonstatistical test) | — | Carvalho et al. [34] |
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Conservation status | Verify the impact of human use in mangroves | Potential | Observed levels of human use | Reduction on species richness | Environmental | Delabie et al. [35] |
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Conservation status | Inventory the ant community in the Baturité hills | Yes | None | Inventory (nonstatistical test)* | — | Hites et al. [36] |
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Conservation status | Study the ant communities in preserved and impacted savanna sites | Yes | Observed human interference | Reduction of diversity in impacted sites * | Environmental | Ramos et al. [37] |
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Fire | Test the negative effect of fire in Restinga environments on the ant community | Potential | Presence of fire | Increase in species richness with presence of fire (mean and confidence intervals of estimated species richness) | Environmental | Endringer et al. [38] |
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Fire | Test the hypothesis that ant species richness and composition change after burning sand dunes | Yes | History of fire | More ant species and distinct species composition in the unburned area (non-statistical test) | Environmental | Teixeira et al. [39] |
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Fragmentation | Verify the responses of ants nesting in twigs in the litter layer to habitat changes associated with forest fragmentation | Potential | Distance to forest edge, remnant isolation, leaf-litter depth, density of dead twigs, and vegetation (three parameters measured) | Higher species richness ; most ant species had greater nest densities in continuous areas than in remnants, change in species composition with forest edge | Ecological | Carvalho and Vasconcelos [40] |
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Fragmentation | Determine the effect of forest fragmentation on ant communities | Yes | Remnant area, distance to forest edge, vegetation cover of matrix, and vegetation (three parameters measured) | No effect of many fragment characteristics on ant species richness: area , distance core-border . Only tree density had an effect | Ecological | Gomes et al. [41] |
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Fragmentation | Know the community of ants in forest fragments | Yes | Remnant area | No change in species richness with remnant area * | Environmental | Santos et al. [42] |
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Forestry systems | Describe the epigaeic ant communities in Eucalyptus plantations | Yes | Eucalyptus age | No change in species richness with Eucalyptus age | Environmental | Fonseca and Diehl [43] |
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Human land-use | Compare the ant community structure between a crop and a secondary forest | Potential | Land use | Reduction of diversity and equitability and change in species composition (non-statistical test) | Environmental | Castro and Queiroz [44] |
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Human land-use | Compare the impact of different agroecosystems on ant species richness | Yes | Land use | Higher species richness in forest edges and pasture (non-statistical test); coffee crop presented reduced estimated richness | Environmental | Dias et al. [45] |
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Human land-use | Survey of ant and termite fauna in four patches with different vegetation structures and in one open field | Potential | Land use | Change in species richness and composition (non-statistical test) | Environmental | Diehl et al. [46] |
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Human land-use | Test the effects of Restinga soil characteristics on ant communities | Yes (implicit) | Land use, physical and chemical soil properties, and microbial activity | Change in species richness (non-statistical test) and composition (canonical correspondence analysis) | Ecological | Gomes et al. [47] |
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Human land-use | Elucidate ant species richness and community structure associated with the micro basin of Sanga Caramuru-Chapecó | Yes | Habitat type, temperature, and rainfall | Change in species composition (Bray-Curtis Cluster Analysis indicated higher similarity for disturbed areas) and higher richness (observed and estimated) in the native area (sample-based accumulation curves)* | Environmental | Ilha et al. [48] |
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Human land-use | Determine the level of similarity of ant communities in forest areas (three native forest remnants) and an Eucalyptus reforestation | Yes | Land use | Change in species composition (Jaccard index— among Eucalyptus crops versus forest remnants and among forest remnants) | Environmental | Lapola and Fowler [49] |
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Human land-use | To inventory the ant fauna in a Cerrado area and in Eucalyptus plantations with five classes of understory ages | Yes | Eucalypt age | Higher density of species in Cerrado areas than in Eucalyptus (non-statistical test) and estimated species richness similar between areas | Environmental | Marinho et al. [50] |
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Human land-use | Investigate the effect of structural characteristics of the environment on ant communities | Yes | Habitat type | Change in species richness and composition (non-statistical test) | Environmental | Santana-Reis and Santos [51] |
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Human land-use | Test the hypotheses that there was a decrease in ant species richness and a change in the species composition in habitats with more intense soil use | Yes | Land use | Sites with distinct soil use host a differential ant species composition (cluster analysis-Euclidean distance) | Environmental | Schmidt and Diehl [52] |
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Human land-use | Evaluate the effect of collection time (day and night) on ant fauna attracted to baits in areas of Eucalyptus cloeziana (Myrtaceae) and Cerrado (savanna vegetation) | Potential | Land use | Collection time effect was more important to ant fauna structure than the vegetation effect (ordination analyses) | Environmental | Tavares et al. [53] |
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Human land-use and succession | Compare ant diversity under different land-use systems | Yes | Land use and age of succession | Change in density of species (non-statistical test), species richness (sample-based accumulation curves and χ2), and composition (cluster analysis)* | Environmental | Braga et al. [54] |
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Inundation | Document the ant fauna in three different forest types (one annually inundated and two on terra firme) | Potential | Vegetation (several parameters measured) | Change in diversity, similarity, and proportion of different nesting and feeding habitats (non-statistical test) | Ecological | Majer and Delabie [55] |
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Logging | Test the hypothesis that logging affects forest ant fauna by reducing the species richness and changing the composition of ground-foraging ant communities | Yes | Canopy openness, abundance of understory vegetation, and leaf-litter depth | Change in species composition proportion of Pheidole was reduced from 21.4% and 26% in unlogged forest and low-impact logging, respectively, to 14.8% in high-impact logging | Ecological | Kalif et al. [56] |
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Mining | Determine the levels of heavy metals in plants and identify soil organisms of the mesofauna that could be biological indicators of soil quality | Yes | Physical and chemical soil properties and heavy metal content | Decrease in abundance and increase in lead (Pb) accumulation (non-statistical test) | Environmental | Barros et al. [57] |
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Mining | Ant fauna survey and community structure, analyses of the ground-dwelling ants in native vegetation and areas with different inferred copper levels | Yes | Areas with different inferred copper levels | Decrease in species richness with inferred copper levels (non-statistical test) | Environmental | Diehl et al. [58] |
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Restoration (agriculture) | Investigate the recolonization profile of the restored Atlantic Forest | Yes | Age after planting | Increase in species richness (, ANOVA) and change in species composition (ANOSIM, )* | Environmental | Pais and Varanda [59] |
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Restoration (anthropogenic disturbance) | Test the hypothesis that ant fauna is closely related to the structural complexity of habitat | Yes | Age of restoration | Change in species composition (non-statistical test) | Environmental | Coelho et al. [60] |
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Restoration (dredging disturbance) | Evaluating ant bioindication of impacted habitats | Yes | Time since restoration, distance from the impact, and physical properties of soil | Change in species richness: higher in cerrado than in the restoration habitats, and also higher in the ecotone and intermediate zones than on the beach and change in abundance and composition (non-statistical test) | Environmental | Costa et al. [61] |
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Restoration (mining) | Investigate which ants recolonized reclaimed areas in subtropical regions and evaluate the effect of different rehabilitation techniques, comparing results with Australia | Yes | Age of rehabilitation, soil penetrability, number of logs, litter and vegetation measures (three and five parameter, resp.) | Increase in species richness (non-statistical test) and change in composition (PCoA) | Ecological | Majer [62] |
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Restoration (mining) | Evaluate the efficacy of rehabilitation procedures in mining sites on facilitating ant recolonization and compare it with other tropical regions and climatic zones | Yes | Age of restoration, soil penetrability, litter depth, percentage of litter, grass, and herb cover, and vegetation (several parameters measured) | Species richness increased in early ages but slowed in late ages and was smaller than control site (non-statistical test). Distinct species composition in sites at early ages, intermediate ages, and control sites (ordination analyses) | Ecological | Majer [63] |
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Restoration (mining) | Investigate the community structure changes of different rehabilitation techniques | Yes | Rehabilitation technique | Change in species richness (non-statistical test) and composition (cluster analysis) | Ecological | Pereira et al. [64] |
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Road | Test the hypothesis that dirt roads are favourable landing sites for Atta laevigata founding queens. Analyze the importance of litter cover as a proximate cue in nest-site selection | Potential | Presence of dirt roads | The number of colonization attempts in roads was 5 to 10 times greater than that in the adjacent vegetation | Environmental | Vasconcelos et al. [65] |
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Seasonality | Investigate ant diversity and species composition on an island | Yes | Seasonality | Change in species richness and composition with seasonality (non-statistical test)* | Environmental | Schmidt et al. [66] |
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Succession | Examine whether secondary forests of the Brazilian Atlantic Forest act as refugia for forest-adapted species | Yes (implicit) | Age of succession and soil type | Richness and composition of ant assemblages in secondary forests have recovered slowly and have not approached conditions typical to old-growth forests | Environmental | Bihn et al. [67] |
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Succession | Examine bait preferences of litter ants along a successional gradient of forest | Potential | Age of succession | Preference of ants for the type of bait changed along the successional gradient . In young successional stages, N baits attracted more ants than CHO baits, whereas in late successional stages, CHO baits attracted more ants | Environmental | Bihn et al. [68] |
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Succession | Investigate how functional diversity profile changed in a successional gradient | Potential | Age of succession | Increased diversity and change in functional groups (non-statistical test) | Environmental | Bihn et al. [69] |
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Succession | Verify patterns in the structure of ant communities along a successional gradient | Potential | Age of succession | Increased diversity and equitability (non-statistical test) | Environmental | Castro et al. [70] |
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Succession | Compare ant diversity among sites in different successional stages | Potential | Age of succession | Higher diversity in intermediary stage and change in composition (non-statistical test) | Environmental | Leal et al. [71] |
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Succession | Compare the diversity and composition of tree-dwelling ants in different successional stages of a seasonal deciduous forest | Potential | Age of succession | Increase in species abundance and change in species composition (PCA analysis) | Environmental | Neves et al. [72] |
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Succession | Compare the ant species diversity related to successional stage and seasonality | Yes | Age of succession, tree richness and density | Change in species composition (DCA deterrent correspondence analysis, ) | Ecological | Neves et al. [73] |
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Succession | Evaluate the long-term effect of fire on ant species richness | Potential | Presence of fire 15 years before | Change in species composition (cluster analyses-Euclidean distance) | Environmental | Santos et al. [74] |
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Succession | Assess the changes in species richness and composition between relatively pristine habitat and along a forest regeneration gradient | Yes | Age of succession | Increase in species richness (sample-based accumulation curves) and distinct species composition between pristine area and areas at regeneration (ANOSIM, * | Environmental | Silva et al. [75] |
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Succession | Compare the structure of the ground ant communities in areas at different levels of restoration | Yes | Age of succession | Increase in species richness and decrease in abundance , change in species composition (ordination analysis) | Environmental | Vasconcelos [76] |
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Succession | Determine experimentally the effects of selective logging on ground-living ants | Yes | Logging age, canopy cover, litter depth, and understory density | Species richness, evenness, and abundance per plot did not vary among treatments . Most of the species found in the control plots were also present in the logged plots | Ecological | Vasconcelos et al. [77] |
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Urbanization | Compare the thermal tolerances of leaf-cutter ants (Atta sexdens) from colonies inside and outside an urban area | Potential | Temperature | Urban ants support higher temperatures better than rural ones, which present higher rates of mortality | Environmental | Angilletta et al. [78] |
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Vegetation type | Inventory ants | Yes | Habitat type | Change in species richness (non-statistical test)* | Environmental | Diehl et al. [79] |
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Vegetation type | Test how the diversity of one taxa can be a good surrogate of all diversity | Yes | Habitat type | Correlation with other taxa (Pearson correlation coefficients) | Biodiversity | Leal et al. [80] |
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Vegetation type | Compare ant diversity in three different forest stages (primary, reforestation, and secondary) | Potential | Habitat type | Change in diversity and exclusive species (non-statistical test)* | Environmental | Lopes et al. [81] |
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Vegetation type | Compare the ant fauna from forests and nearby patches of savanna (Cerrado) in the Brazilian Amazon. Assess whether there is a difference in the fauna between the ground and lower vegetation strata in both habitats | Potential | Habitat type | Forests host twice as many species as savanna (sample-based rarefaction curves). In both habitats, the ground hosted more species than vegetation (). Distinct species composition between forest and savanna and between ground and vegetation within the same habitat; ant species fidelity and specificity is given by IndVal (see Table 2) | Environmental | Vasconcelos and Vilhena [82] |
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