The Southwest Amazon moist forests (NT0166) is an ecoregion located in the Upper Amazon basin.
The forest is characterized by a relatively flat landscape with alluvial plains dissected by undulating hills or high terraces.[2] The biota of the southwest Amazon moist forest is very rich because of these dramatic edaphic and topographical variations at both the local and regional levels. This ecoregion has the highest number of both mammals and birds recorded for the Amazonian biogeographic realm: 257 with 11 endemic species for mammals and 782 and 17 endemics for birds. The inaccessibility of this region, along with few roads, has kept most of the habitat intact. Also, there are a number of protected areas, which preserve this extremely biologically rich ecoregion.
Location
Mauritia flexuosa, or moriche palm, is an economically important species dominant in some parts of the ecoregion.
The southwest Amazon moist forest region covers an extensive area of the Upper Amazon Basin comprising four sub-basins: (1) both the Pastaza-Marañon and (2) Ucayali River sub-basins drain into the Upper Amazon River in Peru; (3) the Acre and (4) Madre de Dios-Beni sub-basins drain to the east into the Juruá, Purus and Madeira Rivers; which, in turn, feed into the Amazon River lower down in Brazil.[2] The region is bisected north to south between Peru and Brazil by the small mountain range Serra do Divisor. It extends east to the edge of the Purus Arch, or ancient zone of uplift, in the southwestern area of the Brazilian State of Amazonas. It then extends southeast into northern Bolivia and in a narrow band south along the base of the Andes Mountains. Elevations range from 300 metres (980 ft) in the west to 100 metres (330 ft) on the eastern edge of the region.
Landforms present in this region include the upland terra firme (non-flooded) mostly on nutrient-poor lateritic soils, ancient alluvial plains (mostly non-flooded) on nutrient-rich soils, and present alluvial plains (várzea, seasonally flooded) of super-rich sediments renewed with each annual flood.[2] Floristically, distinct lowland humid forest types occur on each of these landforms with the terra firme mature forests and late successional, seasonally flooded forest being the two major types. Permanent swamp forests are common on the alluvial plains. Pockets of nutrient-poor white sand soils are found here that host forests of lower height, a more open forest canopy, and lower alpha diversity, but with many endemics. The forests are mostly dense tropical rain forest, but some patches of open forest exist.
Because the ecoregion covers such a vast area, there are climatic, edaphic and floristic differences within it. Generally, the wetter and less seasonal northern forests (3,000 millimetres (120 in) of rain annually) share only 44 percent of the tree species with forests in the slightly drier, more seasonal southern region. This region receives from 1,500 to 2,100 millimetres (59 to 83 in) of rain annually, in different parts. Temperatures over the year range from 22 to 27 °C (72 to 81 °F).
At first glance, large areas may appear to be homogeneous dense forests with a canopy 30 to 40 metres (98 to 131 ft) high with some emergent trees to 50 metres (160 ft) towering above the canopy.[2] Structurally, this may be the case; however, the species composition reflects much the opposite: tree species variability reaches upwards to 300 species in a single hectare. There are a few exceptions to this high diversity, mainly where stands dominated by one or several species occur. The first are vast areas (more than 180,000 square kilometres (69,000 sq mi)) dominated by the highly competitive arborescent bamboos Guadua sarcocarpa and Guadua weberbaueri near Acre, Brazil extending into Peru and Bolivia. Other monodominant stands include swamp forests of the economically important palms Mauritia flexuosa and Jessenia bataua.
Leopardus pardalis, the ocelot, is a threatened species that finds a home in the southwest Amazon moist forests.
What is distinctive about this region is the diversity of habitats created by edaphic, topographic and climatic variability. Habitat heterogeneity, along with a complex geological and climatic history has led to a high cumulative biotic richness. Endemism and overall richness is high in vascular plants, invertebrates and vertebrate animals.[2] This is the Amazon Basin's center of diversity for palms. The rare palm Itaya amicorum is found on the upper Javari River. This ecoregion has the highest number of mammals recorded for the Amazonian biogeographic realm: 257 with 11 endemics. Bird richness is also highest here with 782 species and 17 endemics. In the southern part of the Tambopata Reserve, one area that is 50 square kilometres (19 sq mi) holds the record for bird species: 554. On the white sand areas in the north, plants endemic to this soil type include Jacqueshuberia loretensis, Ambelania occidentalis, Spathelia terminalioides, and Hirtella revillae.
In the region of Manu, 68 species of reptiles and 68 species of amphibians have been reported for the lowland areas while 113 species of amphibians and 118 species of reptiles are reported from Madre de Dios, including the rare and interesting pit-vipers (Bothrops bilineatus, Bothrops brazili), and frogs such as Dendrophidion sp., Rhadinaea occipitalis, and Xenopholis scalaris.[2]
Much of the natural habitat of the region remains intact, protected by sheer inaccessibility.[2] People have dwelled along the major rivers for millennia and have subtly altered the forests on a small scale, but around the urban centers development proceeds. Very few roads exist in the region, limiting development. Intense deforestation is constrained to the few roads that do exist or around urban centers such as Iquitos, Puerto Maldonado, and Rio Branco.
The invasiveGuadua bamboo is threatening the natural ecodiversity of the region.
Hunting may be threatening populations of the tapir (Tapirus terrestris) and large primates in the north.[2] Some habitat is threatened by expansion of the agricultural and pastoral frontier, gold mining, and selective logging that erodes the genetic diversity of a few valuable timber species. The economically important palm Euterpe precatoria is being depleted in some areas by unsustainable palm heart extraction. A dramatic problem that exists in the Brazilian State of Acre and in the adjacent area of Peru is the spread of the invasiveGuadua bamboo forests. This highly competitive bamboo invades and dominates abandoned clearings and threatens to dominate the disturbed areas in this region. Logging along major rivers and near urban centers has decimated populations of mahogany (Swietenia macrophylla), tropical cedar (Cedrela odorata), and kapok (Ceiba pentandra).
During the period from 2004 to 2011 the ecoregion experienced an annual rate of habitat loss of 0.17%.[5]
Coca-Castro, Alejandro; Reymondin, Louis; Bellfield, Helen; Hyman, Glenn (January 2013), Land use Status and Trends in Amazonia(PDF), Amazonia Security Agenda Project, archived from the original(PDF) on 19 March 2016, retrieved 24 March 2017
WildFinder, WWF: World Wildlife Fund, retrieved 11 March 2017
Further reading
Daly, D. C., and J. D. Mitchell. 2000. "Lowland vegetation of tropical South America". Pages 391–453 in D. L. Lentz, editor, Imperfect Balance: Landscape Transformations in the Precolumbian Americas. New York: Columbia University Press. ISBN0-231-11156-8
Ducke, A.; Black, G. A. (1953). "Phytogeographical Notes on the Brazilian Amazon". Anais da Academia Brasileira de Ciências. 25: 1–46.
Ergueta S.P., and J. Sarmiento. 1992. "Fauna silvestre de Bolivia: diversidad y conservación". Pages 113–163 in M. Marconi, editor, Conservación de la Diversidad Biológica en Bolivia. La Paz, Bolivia: CDC-Bolivia and USAID.
Fundação Instituto Brasilero de Geografia Estatástica-IBGE. 1993. Mapa de vegetação do Brasil. Map 1:5,000,000. Rio de Janeiro, Brazil.
Henderson, A. 1995. The Palms of the Amazon. New York: Oxford University Press. ISBN0-19-508311-3
Instituto Geográfico Nacional. 1987. Ecoregiones del Peru. Map 1:5,000,000. Atlas del Peru, Lima, Peru.
Pacheco, V., and E. Vivar. 1996. "Annotated checklist of the non-flying mammals at Pakitza, Manu Reserve Zone, Manu National Park, Perú." Pages 577–592 in D. E. Wilson and A. Sandoval, editors, Manu: The Biodiversity of Southeastern Peru. Washington, DC: Smithsonian Institution.
Peres, C. A. 1999. "The structure of nonvolant mammal communities in different Amazonian forest types". Pages 564–581 in J. F. Eisenberg and K. H. Redford, editors, Mammals of the Neotropics: the Central Neotropics. Chicago: University of Chicago Press. ISBN0-226-19542-2
Räsänen, M. 1993. "La geohistória y geología de la Amazonia Peruana". Pages 43–67 in R. Kalliola, M. Puhakka, and W. Danjoy, editors, Amazonia Peruana: vegetacióon húmeda tropical en el llano subandino. Turku: PAUT and ONERN.
Ribera Arismendi, M. 1992. "Regiones ecológicas." Pages 9–71 in M. Marconi, editor, Conservación de la Diversidad Biológica en Bolivia. La Paz, Bolivia: CDC-Bolivia and USAID.
Ribera, M.O., M. Libermann, S. Beck, and M. Moraes. 1994. Mapa de la vegetacion y areas protegidea de Bolivia. 1:1,500,000. Centro de Investigaciones y Manejo de Recursos Naturales (CIMAR) and Universidad Autónoma Gabriel Rene Moreno (UAGRM), La Paz, Bolivia.
Silva, J.M. C. 1998. Um método para o estabelecimento de áreas prioritárias para a conservação na Amazônia Legal. Report prepared for WWF-Brazil. 17 pp.