Three parks, the same tools: Great Smoky, Gros Morne and Iguaçu
A national park in the United States, one in Canada and one in Brazil, of similar size, read with the same tools: the official outline, tree-cover loss, land use and what GBIF holds on birds, plants and mammals. It is neither a ranking nor a proof: the story shows where the tools work the same in all three countries and where the parks differ, in the land around them, the kind of observation and the quantity of records, and why a count of records measures observation effort, not richness.
Loading the numbers…
—bird, plant and mammal records per km² in Great Smoky (GBIF) measured
—the same in Gros Morne measured
—the same in Iguaçu measured
measured by satellite, the official outline or a GBIF count.
estimated a reading that depends on a choice.
missing a part that could not be obtained.
1
The same outline, the same ruler
Great Smoky Mountains (United States), Gros Morne (Canada) and Iguaçu National Park (Brazil) are national parks, all in IUCN category II. The three outlines come from the same world database, the WDPA, and the area was recomputed from the polygon. The three appear side by side, at the same scale, and the “Highlight” buttons pick out one of them in every step.
2
Four identical tools and one map that changes by country
Four things run with no change in all three countries: the outline (WDPA), the satellite image (Sentinel-2), tree-cover loss (Hansen) and the count of records (GBIF). One changes from country to country by necessity: the land-use map, which each country produces with its own method and legend. The table says which.
3
Quantity: the same question, very different numbers
GBIF adds up what museums, herbaria, observers and cameras have published. Each row is what exists inside each park's outline for one group: records, species and records per km². A record is someone's encounter with a species at a place and a date; many records say, first of all, where people were looking.
4
The map of records is the map of who looked
Each square is a 0.05° cell (about 5 km), coloured by the density of records of birds, plants and mammals inside the park. The literature shows that records cluster near roads and towns, and far from them there are rarely visited areas, even when the park is the same.
5
Sighting, specimen or machine
GBIF separates collection specimens, human observations and machine observations (cameras and recorders). All three count but say different things: a specimen has a name and a place that can be checked in a collection; a human observation depends on who saw it and who identified it.
6
Who is behind the records
Behind every number there is a dataset, with a publisher and its own citation on GBIF. The largest ones in each park show what kind of science produces them: bird-observation platforms, naturalists, or museum collections and institutional inventories.
7
Records by year
Records do not grow evenly through time: citizen-observation platforms pushed the number of records up in recent decades, and not every park followed the same pace. The chart shows records per km² per year, for the three groups together.
8
Inside and outside, measured the same way
Hansen counts all tree-cover loss since 2001, from any cause: fire, storm, pests, felling. Applied to the inside of each park and to a 10 km ring around it, it shows where the land changed, without saying why. The map colours mark the period in which each pixel lost its cover.
9
What each country maps around it, in 1985 and today
Each country has its own annual land-cover map, with its own method and legend, and the three are not added together. In the United States it is the Annual NLCD, 1985 and 2024; in Canada, the NTEMS VLCE2, 1985 and 2022, chosen for Gros Morne because it has forest, shrub, wetland and water classes, the ones that count in a park of forest, bog and coast, with the limits that it ends in 2022 and has no built-up or cropland class; in Brazil, MapBiomas Collection 11, 1985 and 2024, with classes of its own, such as mosaic of uses and forestry, that the other two maps lack. So the three parks’ tables should not be read side by side. Drag the bar: it moves the three panels together.
10
The species GBIF records in each park
Without the official lists, we can read what GBIF records inside each outline: how many species of each group and how many appear in only one park. It is a list of what was recorded, not of what exists, built from GBIF’s own species count and the names from its species API.
11
Whom people meet, and what is found in one park only
The most recorded species in each park say what is easy to see and identify; those found in only one park show what is local to the outline. The names and common names come from GBIF’s species API.
12
What the IUCN category on GBIF indicates
GBIF attaches to each species its IUCN Red List category, when the species has been assessed: it is the one threat yardstick the three countries share. Here species (not records) are counted in the CR, EN, VU and NT categories inside each outline. It is not an official park list: it is GBIF’s name match with the IUCN.
13
Extinct, extinct in the wild, data deficient: which species they are
Some categories look odd on a list of a park’s living species: extinct, extinct in the wild, conservation dependent and data deficient. Instead of dropping them, we looked at which species they are and whether the names are accepted in GBIF’s catalogue, to say what is known and what is not.
14
How many species the official sources say there are
Totals published by each agency, as context and not as a comparison: each source has a different scope, method and date. Great Smoky comes from NPS pages and an inventory of all taxa; Iguaçu from an ICMBio bird guide and a scientific survey of mammals; for Gros Morne, the Parks Canada and IUCN pages carry no totals for birds or plants. Ecology expects more species in tropical forests than in temperate and boreal ones (the latitudinal diversity gradient); this table does not test that, because the numbers have different methods and there are empty cells. An expected difference between biomes, not a result of this story.
15
The comparison with the official lists is still missing
The idea was to compare GBIF with each park's official species list, and with the national threatened-species lists: how many listed species have at least one record, and how recent and precise. In this round those lists could not be obtained, species by species, in machine-readable form (what could be read were the totals of the previous step); the table says what was tried and what stopped it. The per-species lists in the previous steps come from GBIF and are not official. Nothing was made up to fill the gap.
16
The same forest, seen close up in another story
The Iguaçu polygon falls entirely in IBGE's Atlantic Forest biome. The story of the Mello Leitão museum, in Santa Teresa (Espírito Santo), reads the same biome with the same tools from a very different point of view: four small places instead of one park, and what GBIF holds for each, with the location and precision of the records.
umaterra.com.br · Great Smoky · Gros Morne · Iguaçu
Loading…measured
Loading the numbers…
What this story does not say
Counting records is not counting species or comparing parks. GBIF measures observation effort: where there are people, platforms and collections, there are records. Two parks with very different numbers can hold the same life with different effort; this is why the story does not rank the parks or say which is richer.
Three groups, not all of life. Birds, plants and mammals are the most recorded groups and the easiest to compare, and that is part of the bias: insects, fungi and soil life hardly appear.
The GBIF polygon is a simplified version. GBIF receives the outline through an address of limited size; each outline was simplified only until it fitted, and the area difference stayed below 0.1% (the exact values are in the data). Inner holes (properties inside the park) were also removed.
Canopy loss is not deforestation. Hansen counts all tree-cover loss, whether from fire, storm, pests or felling, and counts any pixel with a loss year, even with little canopy in 2000: the proportions are indicative. What caused the loss inside each park was not investigated here.
Three land-cover maps, three methods. The Annual NLCD, MapBiomas and NTEMS VLCE2 have different legends, years and purposes and were not mixed. VLCE2 has no built-up class: at Gros Morne development is not measured, and we do not claim it does not exist. Gros Morne's 10 km ring includes open sea, which appears as water.
Official lists are not in this version. The official lists of each park and the national threatened-species lists could not be obtained in machine-readable form; the page claims nothing about how many listed species have a record. The per-species lists come from GBIF and are not official; the only threat yardstick shown is the IUCN category GBIF attaches to species, and some of those categories look odd (previous steps).
The official totals are not comparable with each other. Each number has its own source, date, scope and method (an all-taxa inventory, a leaflet, a scientific survey, a whole island), and some cells have no number: the table is context, not a measure of richness. The expectation of more species in the tropics comes from the literature, not from these data.
The park border is that of an official register, not of the map. The outline is the WDPA’s, simplified by 20 m only for drawing (the first version, at 300 m, strayed up to 576 m from the original outline, and was replaced). Official protected-area outlines are more generalised than a 30 m map: the Iguaçu one in the CNUC register has 704 vertices. So the forest edge in the land-cover maps may not coincide with the park border; the layer placement was checked against a latitude-longitude grid (placement error at most 1 pixel, about 86 m), and measuring how closely the forest follows the border was left undone.
GBIF is not the park's own collection. The data the parks' own teams hold, and many records never published, do not appear here.
Written with Claude Sonnet 5.5, by Anthropic, from the cited papers and the numbers Earth Engine and GBIF returned: no fact or number comes from the model. Versão em português.
Notes and references
Hortal, J., de Bello, F., Diniz-Filho, J. A. F. et al. (2015). Seven shortfalls that beset large-scale knowledge of biodiversity. Annual Review of Ecology, Evolution, and Systematics 46, 523–549. doi:10.1146/annurev-ecolsys-112414-054400.
Boakes, E. H., McGowan, P. J. K., Fuller, R. A. et al. (2010). Distorted views of biodiversity: spatial and temporal bias in species occurrence data. PLoS Biology 8(6), e1000385. doi:10.1371/journal.pbio.1000385.
Troudet, J., Grandcolas, P., Blin, A. et al. (2017). Taxonomic bias in biodiversity data and societal preferences. Scientific Reports 7, 9132. doi:10.1038/s41598-017-09084-6. This is why the story is limited to birds, plants and mammals and does not compare the groups with each other.
Heberling, J. M., Miller, J. T., Noesgaard, D. et al. (2021). Data integration enables global biodiversity synthesis. Proceedings of the National Academy of Sciences 118(6), e2018093118. doi:10.1073/pnas.2018093118.
Hansen, M. C., Potapov, P. V., Moore, R. et al. (2013). High-resolution global maps of 21st-century forest cover change. Science 342, 850–853. doi:10.1126/science.1244693. Version v1.13 (loss 2001–2025), read in Earth Engine; tree-cover loss from any cause, in any pixel with a loss year; the 2000 cover is that of pixels with at least 30% canopy.
Souza, C. M., Shimbo, J. Z., Rosa, M. R. et al. (2020). Reconstructing three decades of land use and land cover changes in Brazilian biomes with Landsat archive and Earth Engine. Remote Sensing 12(17), 2735. doi:10.3390/rs12172735. MapBiomas Collection 11, 1985 and 2024, climate-shift groups.
Hermosilla, T., Wulder, M. A., White, J. C. et al. (2018). Disturbance-informed annual land cover classification maps of Canada’s forested ecosystems for a 29-year Landsat time series. Canadian Journal of Remote Sensing 44(1), 67–87. doi:10.1080/07038992.2018.1437719. NTEMS VLCE2 (1984–2022), 1985 and 2022. It is a forest-oriented map: it has no built-up or cropland class, so it does not measure development.
U.S. Geological Survey. Annual National Land Cover Database (Annual NLCD), Collection 1, 1985 and 2024, read through Earth Engine and climate-shift. mrlc.gov.
UNEP-WCMC and IUCN. Protected Planet: the World Database on Protected Areas (WDPA), Earth Engine asset WCMC/WDPA/current/polygons, read on 2 Nov 2026; filtered by country, name and designation (Great Smoky Mountains: National Park; Gros Morne National Park of Canada: National Park; Parque Nacional do Iguaçu: Park). protectedplanet.net.
Copernicus Sentinel-2, harmonised level 2A (COPERNICUS/S2_SR_HARMONIZED), 2024 median in each park (Jun–Sep at Smoky, Jul–Sep at Gros Morne, May–Sep at Iguaçu), clouds, shadows and cirrus masked. sentinels.copernicus.eu.
GBIF.org occurrence search, facet counts with no records downloaded, with hasCoordinate=true and hasGeospatialIssue=false, inside each park's simplified polygon (the simplification, in degrees, is in the data), on the date shown at the top of the page. Each record carries the citation of the dataset that published it on gbif.org. Groups: birds (class Aves), plants (kingdom Plantae), mammals (class Mammalia).
Lists sought on 2 Nov 2026 and not obtained: the Great Smoky species list in NPSpecies (irma.nps.gov/NPSpecies; the data service answered 503, and the page is dynamic); the Gros Morne list from Parks Canada (the address answered 404) and the federal species-at-risk registry (SARA); the Iguaçu list from ICMBio and Portaria MMA no. 148/2022 (the server refused automated access, 403); the IUCN Red List (403 refusal; the API requires a token and acceptance of terms).
IBGE. Biome domains 1:250,000 (asset ibge_biome_domain_250k, the same one Naturametrics' biome selector reads), intersected with the Iguaçu polygon. ibge.gov.br.
U.S. National Park Service. Great Smoky Mountains National Park, Nature (updated 22 Dec 2022), Plants (26 Mar 2026), Birds (23 Jan 2026) and Mammals (10 Jun 2026) pages, read on 2 Nov 2026: nature, plants, birds, mammals. The pages say “species documented”; plants include the non-vascular ones.
Parque Nacional do Iguaçu, ICMBio and Cataratas do Iguaçu S.A. Guia de aves (leaflet), read on 2 Nov 2026: gov.br/icmbio. The leaflet gives 348 bird species, 26 threatened with extinction; it has no date or method.
Brocardo, C. R., Silva, M. X., Ferracioli, P. et al. (2019). Mamíferos do Parque Nacional do Iguaçu. Oecologia Australis 23(2), 165–190. doi:10.4257/oeco.2019.2302.01. 84 species of wild mammals (three exotic) and 18 more with potential distribution.
Parks Canada. Gros Morne National Park — Wildlife, read on 2 Nov 2026 (the island of Newfoundland has fourteen native mammals): parks.canada.ca; IUCN. World Heritage Outlook, Gros Morne National Park (the park's vascular plants and bryophytes make up about 60% of Newfoundland's island flora): worldheritageoutlook.iucn.org.
Hillebrand, H. (2004). On the generality of the latitudinal diversity gradient. The American Naturalist 163(2), 192–211. doi:10.1086/381004.
Parks Canada. Gros Morne National Park — Spruce budworm, read on 2 Nov 2026: budworm numbers have been rising on Newfoundland's west coast since 2018, with widespread defoliation in 2021 and, by 2024, lowland forest affected across much of the park. parks.canada.ca.
GBIF.org, occurrence search (facet counts by speciesKey, with and without the iucnRedListCategory filter, no records downloaded) and species API (api.gbif.org/v1/species), on 2 Nov 2026, for the same simplified polygons and filters as the GBIF counts above. The IUCN category is the one GBIF attaches to the species’ accepted name; it was not checked at the IUCN source. gbif.org.