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How Habitat Change and Rainfall Affect Dung Beetle Diversity in Caatinga, a Brazilian Semi- Arid.. Professor Moraes Rego s/n, Cidade Universit. Professor Moraes Rego s/n, Cidade Universit. Professor Moraes Rego s/n, Cidade Universit. The communities were sampled monthly from May 2. April 2. 00. 7 using pitfall traps baited with human feces in two environments denominated “land use area” and “undisturbed area.” Abundance and species richness were compared between the two environments and two seasons (dry and wet season) using a generalized linear model with a Poisson error distribution. Diversity was compared between the two environments (land use area and undisturbed area) and seasons (dry and wet) using the Two- Way ANOVA test. Non- metric multidimensional scaling was performed on the resemblance matrix of Bray- Curtis distances (with 1. Spearman's correlation coefficient was used to determine whether rainfall was correlated with abundance and species richness. A total of 1. 09. The most abundant and frequent species was Dichotomius geminatus Arrow (Coleoptera: Scarabaeidae). Seed Germination and Seedling Development of Anadenanthera Colubrina in Response to Weight and Temperature Conditions. The caatingas dominium. Revista Brasileira de Bot. Plant species and habitat structure in a sand dune field in the brazilian Caatinga: a homogeneous habitat harbouring an. The caatingas dominium. The Caatingas dominium. Revista Brasileira de Bot. Present-day forest refuges in northeastern. The caatingas dominium. ESRI, 1998.Arcview GIS 3.1. Land mosaics: the ecology of landscapes. The caatingas dominium. PDF (315 KB) Article Components. BioOne is the product of innovative collaboration between scientific societies. DOMINIUM”: THEORETIC BASES FOR IMPLANTATION OF VEGETAL AND/OR ANIMAL ECOSYSTEMS The semi-arid tropic in the northeastern part of. Chapter I - Introduction to Brazilian Biodiversity THE CONVENTION ON BIOLOGICAL DIVERSITY (CBD): GLOWKA, L.,BURHENNE-GUILMIN, F., SYNGE. The Caatingas Dominium. Revista Brasileira de Bot Flowering plants of the Grota do Angico Natural Monument, Caatinga of Sergipe. The Caatingas dominium. Pdf in English; ReadCube Article in xml format; Article references; How to cite this article: Curriculum. The caatingas dominium. Revista Brasileira de Bot. Official Full-Text Publication: Floristic composition of the shrubland decidual vegetation at Ibimirim district, Pernambuco, Brazil on ResearchGate, the professional network for scientists. The environment exerted an influence over abundance. Abundance and diversity were affected by season, with an increase in abundance at the beginning of the wet season. The correlation coefficient values were high and significant for abundance and species richness, which were both correlated to rainfall. In conclusion, the restriction of species to some environments demonstrates the need to preserve these areas in order to avoid possible local extinction. Therefore, in extremely seasonable environments, such as the Caatinga, seasonal variation strongly affects dung beetle communities. Keywords. : dry season, human impact, Scarabaeinae. Introduction. Tropical deforestation is an important process that contributes to the present- day concern for the loss of biodiversity and increased rates of species extinction (Didham et al. With the expansion and consolidation of agricultural frontiers, species that survive in habitat remnants are confronted with a modified environment immersed in environmentally harsh matrices, such as pastures and croplands (Gascon et al. Tabarelli et al. Such changes directly influence the number of species and size of populations by affecting biotic interactions, the amount of available resources and the extent of variations in the physical environment (Schiffler 2. In northeastern Brazil, between 3. Caatinga ecosystem has been altered by human activities (Leal et al. Inappropriate land use has caused serious environmental harm and the accelerating process of desertification is currently threatening about 1. Caatinga region (Leal et al. Moreover, the rich, diversified biota of Caatinga is poorly protected, with only 1. Leal et al. With growing pressure of human development on natural resources, identifying and making use of ecological indicators is an essential task in the conservation of tropical ecosystems (Uehara- Prado et al. Dung beetles play an important role in tropical ecosystems with regard to the recycling of soil nutrients (Bornemissza and Williams 1. Estrada and Estrada 1. Avenda. 2. 00. 5, Quintero and Roslin 2. These beetles have been widely proposed as an ideal group for biodiversity inventories and monitoring, as they satisfy all of the criteria of a focal taxon and have been used in ecological research, biodiversity surveys and conservation work in many regions of the world (Spector 2. Dung beetles are found in defined guilds that are functionally and taxonomically dependent upon the environment. Such guilds are established according to the strategy used for allocating feeding or nesting resources (telecoprids, paracoprids and endocoprids), the degree of dietary specialization (coprophagous, necrophagous, saprophagous, mycetophagous, myrmecophilous, predatory or generalist) and the temporal pattern of their activity (diurnal, nocturnal, twilight or continuous) (Halffter and Matthews 1. Cambefort and Hanski 1. Halffter and Favila 1. Hern. 2. 00. 7, Gardner et al 2. Larsen et al. 2. 01. Filgueiras et al. Micro- environmental variations in soil texture, humidity and forest structure affect the occurrence and relative abundance of these communities (Spector and Ayzama 2. The destruction of the natural environment for the conversion of such areas into pastures or monocultures alters local abiotic factors, which affect both the population structure and composition of the beetle community (Medri and Lopes 2. These changes decrease evenness in the community, leading to the dominance of some species, as most interior forest species cannot tolerate the conditions offered by deforested areas (Davis et al. Such patterns have mainly been observed in tropical rainforests. However, studies involving dung beetles are scarce (Andresen 2. Hern. These beetles are also affected by seasonal changes in rainfall (Hanski and Cambefort 1. Andresen 2. 00. 5). The aim of the present study was to compare dung beetle communities in a land use area and an undisturbed area in the Caatinga and answer two questions: (1) how does forest disturbance and rainfall affect dung beetle communities in their abundance, species richness, and diversity? The area is part of the Sertaneja depression, corresponding to the largest geomorphological feature of the semiarid region, which consists of a large depressed plain bordered by elevated areas and mountain ranges (Andrade- Lima 1. This Brazilian ecosystem is known as the Caatinga and consists of patches of seasonally dry forest and sclerophyllous vegetation (sensu. Pennington et al. Brazil (Sampaio 1. Since 2. 00. 2, Catimbau National Park has been a Federal Conservation Unit. This designation was given to preserve the geological, speleological and archeological features as well as to protect one of the last preserved areas of Caatinga. The climate is defined as hot semiarid (BSh—according to the K. The temperature can reach as high as 4. Rainfall occurs between March and July (ITEP 2. In the present study, months with rainfall indices greater than 6. These data were provided by the Brazilian Geological Service. Location of the study area, Caatinga area of Catimbau National Park, Northeastern Brazil. High quality figures are available online. Methodology. Dung beetle communities were sampled monthly from May 2. April 2. 00. 7 (except February 2. The land use area was used for raising cattle in the dry season and corn farming in the wet season. The undisturbed area is a preserved area in which there has been no constant tree cutting or livestock raising. Three areas spaced 4. Pitfall traps consisted of a plastic container (9. The traps were buried in the soil at the end of the day, protected by a suspended polystyrene disk and remained exposed for 4. Six traps were deployed in each area, distributed randomly but at a minimal distance of 1. A total of 3. 96 samples were collected (six traps . The insects collected were incorporated into the Entomology Collection of the Universidade Federal de Pernambuco (Brazil). Data analysis. The dung beetle communities were studied with respect to abundance, species richness, equitability (Camargo index) and diversity . Abundance and species richness were compared between the two environments (land use area and undisturbed area) and seasons (dry and wet) using generalized linear models with a Poisson error distribution. The dung beetle communities were studied using abundance, species richness, equitability (Camargo index), and diversity data . Camargo's index (E ') is not affected by species richness and is used when you want rare and common species have equivalent weight in the sample. Diversity was compared between the two environments (land use area and undisturbed area) and seasons (dry and wet season) using the Two- Way ANOVA test. The estimation of these indices was performed using the Ecological Methodology 5. Rarefaction curves for the land use area and undisturbed area were constructed using individual- based rarefaction (Gotelli and Colwell 2. Non- metric multidimensional scaling was performed on the resemblance matrix of Bray- Curtis distances, with 1. The species abundance data were transformed (square root) and standardized (sensu Clarke and Gorley, 2. Analysis of similarities (Clarke, 1. Bray- Curtis similarities, with 9. Finally, Spearman's correlation coefficient was used to determine whether rainfall was correlated with abundance and species richness. Results. A total of 1. In the undisturbed area, 3. In the land use area, 7. No differences in the diversity index or Camargo equitability index were found between the two environments (F = 0. F = 0. 7. 8, df = 1, p = 0. A total of 1. 02. Significant differences were found in abundance (F = 3. Moreover, a significant difference was found in diversity index values between seasons (F = 2. Significant differences in abundance (F = 4. However, even though the land use area exhibited higher species richness than the undisturbed area (Figure 2), the generalized linear model did not identify distinction in terms of dung beetle species richness. Individual- based rarefaction curves for dung beetles in land use area (dots) and undisturbed area (line), in two environments of Catimbau National Park, North. High quality figures are available online. Only Dichotomius geminatus Arrow (Coleoptera: Scarabaeidae) occurred in every sample and was the most abundant species found at both sites (7. Only 2. 3. 0. 8% of the species were rollers and 7. Scarabaeinae gilds, number of specimens, and relative abundance (%) of Scarabaeinae species present in two environments of Catimbau National Park, Northeastern Brazil. WS: wet season, DS: dry season. The non- metric multidimensional scaling results for the dung beetle communities clearly revealed different species composition and community structure (abundance data) between the land use area and the undisturbed area, with the exception of one undisturbed area (Figure 3). These results were confirmed by analysis of similarities (global R = 0. R = 0. 7. 0; p< 0.
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