Xenarthrans—anteaters, sloths, and armadillos—have essential functions for ecosystem maintenance, such as insect control and nutrient cycling, playing key roles as ecosystem engineers. Because of habitat loss and fragmentation, hunting pressure, and conflicts with domestic dogs, these species have been threatened locally, regionally, or even across their full distribution ranges. The Neotropics harbor 21 species of armadillos, 10 anteaters, and 6 sloths. Our data set includes the families Chlamyphoridae (13), Dasypodidae (7), Myrmecophagidae (3), Bradypodidae (4), and Megalonychidae (2). We have no occurrence data on Dasypus pilosus (Dasypodidae). Regarding Cyclopedidae, until recently, only one species was recognized, but new genetic studies have revealed that the group is represented by seven species. In this data paper, we compiled a total of 42,528 records of 31 species, represented by occurrence and quantitative data, totaling 24,847 unique georeferenced records. The geographic range is from the southern United States, Mexico, and Caribbean countries at the northern portion of the Neotropics, to the austral distribution in Argentina, Paraguay, Chile, and Uruguay. Regarding anteaters, Myrmecophaga tridactyla has the most records (n = 5,941), and Cyclopes sp. have the fewest (n = 240). The armadillo species with the most data is Dasypus novemcinctus (n = 11,588), and the fewest data are recorded for Calyptophractus retusus (n = 33). With regard to sloth species, Bradypus variegatus has the most records (n = 962), and Bradypus pygmaeus has the fewest (n = 12). Our main objective with Neotropical Xenarthrans is to make occurrence and quantitative data available to facilitate more ecological research, particularly if we integrate the xenarthran data with other data sets of Neotropical Series that will become available very soon (i.e., Neotropical Carnivores, Neotropical Invasive Mammals, and Neotropical Hunters and Dogs). Therefore, studies on trophic cascades, hunting pressure, habitat loss, fragmentation effects, species invasion, and climate change effects will be possible with the Neotropical Xenarthrans data set. Please cite this data paper when using its data in publications. We also request that researchers and teachers inform us of how they are using these data.

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) indicated the establishment of a herbivorous food web structure. Particulate organic carbon (POC) production was mainly due to phytoplankton (98%) and did not differ between periods. However, the observed variability in plankton trophic interactions should affect the magnitude of POC export from this dynamic system. KEY WORDS: Food webs · Carbon fluxes · Bacterioplankton · Phytoplankton · Zooplankton · Cabo Frio · South Brazil Bight Resale or republication not permitted without written consent of the publisherMar Ecol Prog Ser 363: [109][110][111][112][113][114][115][116][117][118][119] 2008 small phytoplankton and bacteria to larger zooplankton and then higher pelagic trophic levels is mediated by heterotrophic nano-and micro-sized protists (Sherr et al. 1986). Therefore, in these microbial food webs, most of the biogenic carbon produced is recycled within the system through heterotrophic respiration (Legendre & Le Fevre 1995).In contrast, in more eutrophic systems with low vertical stability, larger phytoplankton cells are more representative and usually dominant, where turbulence simultaneously provides nutrient and prevents sinking below the euphotic zone (Kiørboe 1993). In those conditions an herbivorous food web prevails and most of the POC produced is exported via grazing, as the mesozooplankton are the dominant primary consumers (Legendre & Rassoulzadegan 1996). Moreover, carbon export is directly related to the input and uptake of 'new' nutrients, mainly nitrate (N-NO 3 ) to the euphotic zone (Dugdale & Goering 1967), and this nitrogen form is primarily utilized by larger cells, such as diatoms (Price et al. 1985).Coastal waters influenced by upwelling are among the most productive aquatic systems. The periodical wind-driven transport of surface waters offshore and the consequent upwelling of deeper water masses provide enrichment to previously oligotrophic waters. The high nutrient input to the surface waters, especially N-NO 3 , stimulates phytoplankton production, mainly for larger species, resulting in higher mesozooplankton and fisheries productivity. This pattern has been described for several upwelling zones around the world, such as those in the SE Pacific Ocean , Iriarte & Gonzalez 2004, Fernandez-Alamo & Farber-Lorda 2006, NE Pacific Ocean (Peterson et al. 1979, Collins et al. 2003, NE Atlantic Ocean (Bode et al. 2003), and Indian Ocean (Brown et al. 2002).Upwelling zones usually occur along eastern ocean boundaries, between 30°N and 30°S, due to the dominance of the trade winds. In the SW Atlantic, however, the change in the coastal direction at 23°S (Cabo Frio, SE Brazil) from N-S to E-W, along with the proximity of the 100 m isobath to the coast, allow the NE winds to move surface waters offshore and the consequent upwelling of the South Atlantic Central Water (SACW). This results in a high productivity core in the midst of the otherwise oligotrophic Brazilian Current waters (Valentin 1984a). The upwelling of deeper water masses is reversed when shifts in wind direction bring surface w...