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Environmental Management
https://doi.org/10.1007/s00267-021-01513-7
Large-scale Degradation of the Tocantins-Araguaia River Basin
Fernando Mayer Pelicice 1●Angelo Antonio Agostinho2●Alberto Akama3●José Dilermando Andrade Filho4●
Valter M. Azevedo-Santos5●Marcus Vinicius Moreira Barbosa6●Luis Mauricio Bini7●
Marcelo Fulgêncio Guedes Brito8●Carlos Roberto dos Anjos Candeiro9●Érica Pellegrini Caramaschi10 ●
Priscilla Carvalho11 ●Rodrigo Assis de Carvalho12 ●Leandro Castello13 ●Davi Borges das Chagas14 ●
Carine Cavalcante Chamon15 ●Guarino Rinaldi Colli16 ●Vanessa Salete Daga17 ●Murilo Sversut Dias18 ●
José Alexandre Felizola Diniz Filho7●Philip Fearnside19 ●Wagner de Melo Ferreira1●
Diego Azevedo Zoccal Garcia20 ●Tiago Kutter Krolow21 ●Rodrigo Ferreira Kruger22 ●
Edgardo Manuel Latrubesse23 ●Dilermando Pereira Lima Junior24 ●Solange de Fátima Lolis1●
Fabyano Alvares Cardoso Lopes25 ●Rafael Dias Loyola26 ●André Lincoln Barroso Magalhães27 ●
Adriana Malvasio28 ●Paulo De Marco Jr.7●Pedro Ribeiro Martins29 ●Rosana Mazzoni30 ●João Carlos Nabout12 ●
Mário Luis Orsi20 ●Andre Andrian Padial31 ●Hasley Rodrigo Pereira32 ●Thiago Nilton Alves Pereira15 ●
Phamela Bernardes Perônico12 ●Miguel Petrere Jr.33 ●Renato Torres Pinheiro34 ●Etiene Fabbrin Pires35 ●
Paulo Santos Pompeu36 ●Thiago Costa Gonçalves Portelinha37 ●Edson Eyji Sano38 ●
Vagner Leonardo Macedo dos Santos39 ●Paloma Helena Fernandes Shimabukuro4●Idelina Gomes da Silva40 ●
Lucas Barbosa e Souza41 ●Francisco Leonardo Tejerina-Garro42,43 ●Mariana Pires de Campos Telles44,45 ●
Fabrício Barreto Teresa12 ●Sidinei Magela Thomaz46 ●Livia Helena Tonella47 ●Ludgero Cardoso Galli Vieira48 ●
Jean Ricardo Simões Vitule49 ●Jansen Zuanon50
Received: 21 June 2021 / Accepted: 21 July 2021
© The Author(s), under exclusive licence to Springer Science+Business Media, LLC, part of Springer Nature 2021
Abstract
TheTocantins-AraguaiaBasinisoneofthelargestriversystems in South America, located entirely within Brazilian
territory. In the last decades, capital-concentrating activities such as agribusiness, mining, and hydropower promoted
extensive changes in land cover, hydrology, and environmental conditions. These changes are jeopardizing the basin’s
biodiversity and ecosystem services. Threats are escalating as poor environmental policies continue to be formulated, such
as environmentally unsustainable hydropower plants, large-scale agriculture for commodity production, and aquaculture
with non-native fish. If the current model persists, it will deepen the environmental crisis in the basin, compromising
broad conservation goals and social development in the long term. Better policies will require thought and planning to
minimize growing threats and ensure the basin’s sustainability for future generations.
Keywords Biodiversity ●Conservation ●Policy ●South America ●Sustainability.
Introduction
Among the largest river systems in South America, the
Tocantins-Araguaia basin stands out due to its large drai-
nage area (767,000 km2) and spectacular biodiversity
(Ribeiro et al. 1995; Lucinda et al. 2007). Located entirely
within Brazil, this basin drains a vast area of the Cerrado
savanna and rainforest ecosystems. Two main rivers form
the basin: the Tocantins, characterized by a unique ich-
thyofauna with several exclusive species, and the Araguaia,
with one of the largest and most biodiverse floodplains in
the world (Latrubesse et al. 2019). The Araguaia River is
also one of the few large free-flowing rivers in South
America, which harbors essential areas for biodiversity
conservation (Latrubesse et al. 2019; Martins et al. 2021).
The unique biodiversity of the Tocantins-Araguaia Basin,
however, contrasts with a long history of policies and
initiatives that have induced extensive environmental
*Fernando Mayer Pelicice
fmpelicice@gmail.com
Extended author information available on the last page of the article.
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degradation. Over the past 40 years, the expansion of dams,
croplands, irrigation, mining, and aquaculture induced
extensive changes to land cover, hydrology, and environ-
mental conditions, jeopardizing biodiversity, ecosystems,
and associated services (Coe et al. 2017; Strassburg et al.
2017; Latrubesse et al. 2019).
Large-scale Degradation
Currently, seven large hydroelectric dams regulate the
main channel of the Tocantins River, with many other
dams blocking the course of tributaries (Winemiller et al.
2016;Akama2017). There are plans to build new dams
(ca. 90), mainly in the Araguaia basin (Latrubesse et al.
2019), in addition to waterways and a large-scale water
diversion system between the Tocantins and São Fran-
cisco basins (Daga et al. 2020). The rapid expansion of
agribusiness for soy and other commodities has caused
the loss of ~50% of the Cerrado (Scaramuzza et al. 2017),
and the activity has advanced progressively over remnant
natural areas (Trigueiro et al. 2020). In 2019, pastures
and monocultures covered more than 42% of the basin
(Fig. 1). The Tocantins-Araguaia basin is currently the
most targeted area for expanding agricultural activities,
as stated in the Presidential Decree 8447 of 2015, which
created the MATOPIBA Federal Plan for Development of
the Brazilian Cerrado in the states of Maranhão, Tocan-
tins, Piauí, and Bahia. In the lower portion of the basin,
cattle ranching has led to the clearing of extensive rain-
forest areas (Nepstad et al. 2014). Broad changes in land
use have eliminated riparian forests (Swanson and
Bohlman 2021) and altered hydrological dynamics (Coe
et al. 2009). Moreover, agriculture expansion has dra-
matically increased the use of pesticides (Martinelli et al.
2010), which invariably end up in aquatic ecosystems.
The increasing demand for irrigation has affected regio-
nal water supplies (Morais et al. 2014), leading to
growing water conflicts. Other activities generally over-
shadow mining, but its impacts are severe. The basin
hosts the two largest iron ore deposits globally, the
Carajás mine in Pará State (with 17 billion tons) and the
Serra do Carmo iron deposit in Tocantins State (with 159
billion tons). Future exploitation of these deposits is a
significant threat, as shown by the recent environmental
disasters in southeastern Brazil (Salvador et al. 2020).
Terrestrial and aquatic biodiversity has responded nega-
tively to these impacts, as evidenced by major losses in
fish diversity (e.g., Araújo et al. 2013; Perônico et al.
2020; Pereira et al. 2021; Santana et al. 2021). Fish
constitute a megadiverse and endemic group in the
Tocantins-Araguaia basin with over 700 species (Dagosta
and de Pinna 2019). According to ICMBio (2018), this
basin has 51 threatened fish species, most of them
endemic.
New Threats
Threats are escalating as public policies continue to prior-
itize maximizing economic growth at the cost of environ-
mental sustainability (Pelicice et al. 2017). The recent
expansion of aquaculture is exemplary. Historically, aqua-
culture in Brazil has been based on low standards of socio-
environmental sustainability (Agostinho et al. 2007; Lima
Junior et al. 2018), involving non-native organisms sub-
jected to poor confinement conditions and inadequate man-
agement practices. Government policies have encouraged
the expansion of aquaculture in the Tocantins-Araguaia
basin, particularly in hydroelectric reservoirs. Many aqua-
culture parks have been planned (Lima et al. 2018) and, in
2021, cage aquaculture was authorized in the area impoun-
ded by the Peixe Angical Dam (https://www.gov.br/pt-br/
noticias/agricultura-e-pecuaria/2021/04/liberada-aquicultura-
em-hidreletrica-no-rio-tocantins). The authorization is valid
for 35 years, and it is the first to be issued in the country after
updates in legislation (Federal Decree 10.576 of 2020) that
reassigned responsibilities and facilitated the authorization
process. This grant was issued shortly after the permission
for the farming of the Nile tilapia (Oreochromis niloticus),
an invasive species, in aquaculture cages in Tocantins State
(https://seagro.to.gov.br/noticia/2018/12/6/criacao-de-tilapia-
em-tanque-rede-e-liberada-no-tocantins/). At the same time,
State Decree 337 of 2019 allowed farming non-native fishes
(i.e., grass carp Ctenopharyngodon idella and Nile tilapia) in
the Araguaia basin and other drainage basins in Mato Grosso
State. In Tocantins State, a bill is moving towards a vote
that would allow the cultivation of the striped catfish
(Pangasianodon hypophthalmus)(https://al.to.leg.br/noticia/
gabinete/jorge-frederico/9889/peixe-panga-jorge-frederico-a
presenta-projeto-de-lei-que-autoriza-o-cultivo-no-tocantins),
an Asian fish with high invasive potential that is already
cultivated in other Brazilian states (Garcia et al. 2018). These
initiatives must accelerate the expansion of aquaculture with
non-native fish in the Tocantins-Araguaia Basin.
This episode illustrates how government policies, guided
by short-term economic profits, ignore scientific advice and
the costs of environmental degradation. Non-native organ-
isms are incipient in aquatic ecosystems in this basin (Doria
et al. 2021; Santana et al. 2021), and aquaculture expansion
will change this scenario, triggering species invasions into
other Amazonian drainage basins. The literature on socio-
environmental impacts resulting from aquaculture is vast
(Agostinho et al. 2007;Diana2009;Vituleetal.2009). It
includes the unavoidable escapes and invasions (e.g.,
Azevedo-Santos et al. 2011; Forneck et al. 2021), and direct
Environmental Management
and indirect negative impacts caused by the Nile tilapia
(compiled by Canonico et al. 2005; Pelicice et al. 2014),
striped catfish (compiled by Garcia et al. 2018), and many
possible synergistic effects between non-native species and
other anthropogenic stressors (e.g., Bezerra et al. 2019). The
potential for local biodiversity to boost fish production is
Fig. 1 Land use and land cover (LULC) map of the Tocantins-
Araguaia River Basin, Brazil. The map shows the scenario in 2019,
indicating the area covered by natural vegetation (forest and non-
forests), water and agro-pastoral activities (pastures and crops), and the
location of small (PCH) and large (UHE) hydroelectric dams. Data
source: MapBiomas (2021)
Environmental Management
enormous. Supported by science, many native fish species in
the basin could provide a basis for local initiatives and
markets (Pelicice et al. 2014). There is a research facility
concerned with aquaculture development in the basin
(Embrapa Pesca e Aquicultura, Palmas, Tocantins State),
which could provide adequate expertise and innovation –but
it has focused extensively on using non-native fishes.
The Need for Better Policies
For decades, Brazil has fostered policies that pursue develop-
ment “at any cost”. Previous setbacks have brought severe
consequences for environmental policies (De Sousa et al. 2011;
Fearnside 2016;Latrubesseetal.2017;Dobrovolskietal.
2018), and current trends have had immediate impacts on the
conservation of the Amazon (Ferrante and Fearnside 2019;
Pelicice and Castello 2021). This approach found fertile ground
in the current political scenario, characterized by scientific
denialism and widespread disregard for the environment
(Thomaz et al. 2020). The Tocantins-Araguaia basin proved
highly vulnerable to these trends and setbacks since it has been
historically targeted for economic development (e.g., Fearnside
2001), and has experienced a rapid expansion of human
activities over the last ten years. The persistence of this scenario
will deepen the environmental crisis in the basin, compromis-
ing broad conservation goals (e.g., UNESCO biosphere
reserves for biodiversity hotspots), national policies (e.g., the
National Strategy for Exotic Species and the National Action
Plan for the Conservation of Endangered Species), and inter-
national agreements (e.g., the Convention on Biological
Diversity and the United Nations sustainable development
goals). The costs arising from environmental degradation are
enormous and irreparable, considering the remarkable biodi-
versity and endemism that characterize the basin. Cultural risks
are no less considerable (Doria et al. 2017), threatening
ancestral knowledge and the ways of life of several native and
traditional groups that live in the basin (Lopes et al. 2021), in
addition to archeological and paleontological heritage (Lopes
et al. 2019). Prevailing policies fail to recognize that environ-
mental degradation generates socioeconomic impacts, threa-
tening the persistence of human activities in the long term
(Burger et al. 2012). The impacts and costs include over-
exploitation of hydroelectric resources, loss of freshwater,
pollution, deforestation, soil degradation, and losses caused by
invasive species. In a situation of high environmental degra-
dation (e.g., river regulation, deforestation, biological invasion),
restoration efforts are complex, costly, and sometimes
impracticable, especially in aquatic environments, where eco-
logical impacts are less readily perceptible (Vitule 2009). Cli-
mate change must complicate this scenario (Colli et al. 2020),
with the risk of affecting current policies, intensifying envir-
onmental degradation, and compromising conservation efforts.
We recommend greater caution, responsibility, and
planning when dealing with environmental issues in the
Tocantins-Araguaia basin. Any development in the basin
must account for its high regional biodiversity value to
establish balanced policies combining economic develop-
ment, environmental preservation, the best available scien-
tific knowledge, and the interests of the different social
groups involved. Protected areas are limited in number and
area, especially in the Tocantins River (Azevedo-Santos
et al. 2019), so development policies must incorporate some
basic tenets (Azevedo-Santos et al. 2021). For example,
maintenance of the connectivity and natural flow regimes of
remaining free-flowing rivers (especially in the Araguaia
Basin), more-stringent control of irrigation projects, cli-
matic monitoring, preservation of riparian forests, control of
deforestation in both the savanna and rainforests (especially
in the headwaters), revoking the authorization of aqua-
culture with non-native species, and improving the inspec-
tion and control of these activities. Still necessary to achieve
these goals are integrative and multidisciplinary studies to
explicitly evaluate the impacts of environmental and
anthropic drivers on distinct components of biodiversity
and at different spatial scales, especially because basic and
important knowledge gaps persist (Carvalho and Tejerina-
Garro 2019; Machado et al. 2019; Colli et al. 2020). The
economic importance of this basin is beyond question (i.e.,
production of hydroelectricity and commodities), but it does
not justify the ongoing environmental degradation. The
human-dominated scenario in the Tocantins-Araguaia Basin
provides the ideal candidate to marry the already existing
economic agenda with conservation of remaining ecosys-
tems in ways that can serve as a model for replication
elsewhere. It would be feasible through the involvement and
engagement of a wide base of stakeholders, including local
and indigenous peoples, farmers and ranchers, the hydro-
power industry, academia, the governmental and non-
governmental sectors, and maybe the international com-
munity. At this moment, economic development and bio-
diversity preservation require much better planning to
minimize escalating conflicts and ensure the sustainability
of resources for coming generations.
Acknowledgements The Programa de Pós-Graduação em Biodiversi-
dade, Ecologia e Conservação (PPGBec) at the Universidade Federal
do Tocantins (UFT) supported this initiative. Conselho Nacional de
Desenvolvimento Científico e Tecnológico (CNPq) provided research
grants.
Author Contributions FMP conceived the idea and wrote the first
draft. All authors contributed with writing, development, and revision.
Funding Some authors have been supported by different agencies,
especially Conselho Nacional de Desenvolvimento Científico e Tec-
nológico (CNPq) and Coordenação de Aperfeiçoamento de Pessoal de
Nível Superior (Capes).
Environmental Management
Compliance with Ethical Standards
Conflict of interest The authors declare no competing interests.
Consent to participate All authors consent with the content of
the paper.
Consent for publication All authors consent with the publication of
the paper.
Publisher’s note Springer Nature remains neutral with regard to
jurisdictional claims in published maps and institutional affiliations.
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Environmental Management
Affiliations
Fernando Mayer Pelicice 1●Angelo Antonio Agostinho2●Alberto Akama3●José Dilermando Andrade Filho4●
Valter M. Azevedo-Santos5●Marcus Vinicius Moreira Barbosa6●Luis Mauricio Bini7●
Marcelo Fulgêncio Guedes Brito8●Carlos Roberto dos Anjos Candeiro9●Érica Pellegrini Caramaschi10 ●
Priscilla Carvalho11 ●Rodrigo Assis de Carvalho12 ●Leandro Castello13 ●Davi Borges das Chagas14 ●
Carine Cavalcante Chamon15 ●Guarino Rinaldi Colli16 ●Vanessa Salete Daga17 ●Murilo Sversut Dias18 ●
José Alexandre Felizola Diniz Filho7●Philip Fearnside19 ●Wagner de Melo Ferreira1●
Diego Azevedo Zoccal Garcia20 ●Tiago Kutter Krolow21 ●Rodrigo Ferreira Kruger22 ●
Edgardo Manuel Latrubesse23 ●Dilermando Pereira Lima Junior24 ●Solange de Fátima Lolis1●
Fabyano Alvares Cardoso Lopes25 ●Rafael Dias Loyola26 ●André Lincoln Barroso Magalhães27 ●
Adriana Malvasio28 ●Paulo De Marco Jr.7●Pedro Ribeiro Martins29 ●Rosana Mazzoni30 ●João Carlos Nabout12 ●
Mário Luis Orsi20 ●Andre Andrian Padial31 ●Hasley Rodrigo Pereira32 ●Thiago Nilton Alves Pereira15 ●
Phamela Bernardes Perônico12 ●Miguel Petrere Jr.33 ●Renato Torres Pinheiro34 ●Etiene Fabbrin Pires35 ●
Paulo Santos Pompeu36 ●Thiago Costa Gonçalves Portelinha37 ●Edson Eyji Sano38 ●
Vagner Leonardo Macedo dos Santos39 ●Paloma Helena Fernandes Shimabukuro4●Idelina Gomes da Silva40 ●
Lucas Barbosa e Souza41 ●Francisco Leonardo Tejerina-Garro42,43 ●Mariana Pires de Campos Telles44,45 ●
Fabrício Barreto Teresa12 ●Sidinei Magela Thomaz46 ●Livia Helena Tonella47 ●Ludgero Cardoso Galli Vieira48 ●
Jean Ricardo Simões Vitule49 ●Jansen Zuanon50
1Núcleo de Estudos Ambientais, Universidade Federal do
Tocantins (UFT), Porto Nacional, Brazil
2Programa de Pós Graduação em Ecologia de Ambientes Aquaticos
Continentais (PEA), Universidade Estadual de Maringá (UEM),
Maringá, Brazil
3Museu Paraense Emílio Goeldi, Belém, Brazil
4Grupo de Estudos em Leishmanioses, Instituto René Rachou,
Fundação Oswaldo Cruz (FIOCRUZ), Belo Horizonte, Brazil
5Universidade Estadual Paulista “Júlio de Mesquita Filho”,
Botucatu, Brazil
6Museu de Zoologia e Taxidermia José Hidasi, Universidade
Estadual do Tocantins (Unitins), Porto Nacional, Brazil
7Departamento de Ecologia, Universidade Federal de Goiás (UFG),
Goiânia, Brazil
8Laboratório de Ictiologia, Departamento de Biologia,
Universidade Federal de Sergipe (UFS), São Cristóvão, Brazil
9Laboratório de Paleontologia e Evolução, Curso de Geologia,
Universidade Federal de Goiás (UFG), Aparecida de Goiânia,
Brazil
10 Departamento de Ecologia, Universidade Federal do Rio de
Janeiro (UFRJ), Rio de Janeiro, Brazil
11 Universidade Federal de Goiás (UFG), Goiânia, Brazil
12 Laboratório de Biogeografia e Ecologia Aquática, Universidade
Estadual de Goiás, Anápolis, Brazil
13 Department of Fish and Wildlife Conservation, Virginia
Polytechnic Institute and State University, Virginia, USA
14 Herbário do Tocantins, Núcleo de Estudos Ambientais,
Universidade Federal do Tocantins (UFT), Porto Nacional, Brazil
15 Laboratório de Ictiologia Sistemática, Núcleo de Estudos
Ambientais, Universidade Federal do Tocantins (UFT),
Porto Nacional, Brazil
16 Departamento de Zoologia, Universidade de Brasília, Brasília-
DF 70910-900, Brazil
17 Researcher, Tampa, FL, USA
18 Departamento de Ecologia, Universidade de Brasília (UnB),
Brasília-DF, Brazil
19 Instituto Nacional de Pesquisas da Amazônia (INPA),
Manaus, Brazil
20 Laboratório de Ecologia de Peixes e Invasões Biológicas,
Universidade Estadual de Londrina (UEL), Londrina, Brazil
21 Laboratório de Entomologia, Universidade Federal do Tocantins
(UFT), Porto Nacional, Brazil
22 Universidade Federal de Pelotas (UFPel), Pelotas, Brazil
23 Environmental Sciences Program-CIAMB, Universidade Federal
de Goiás (UFG), Goiânia, Brazil
24 Universidade Federal de Mato Grosso (UFMT), Campus
Universitário do Araguaia, Pontal do Araguaia, Brazil
25 Laboratório de Microbiologia Universidade Federal do Tocantins
(UFT), Porto Nacional, Brazil
26 Fundação Brasileira para o Desenvolvimento Sustentável (FBDS)
& Universidade Federal de Goiás (UFG), Goiânia, Brazil
27 Researcher, Belo Horizonte, Brazil
28 Laboratório de Ecologia e Zoologia (LABECZ), Universidade
Federal do Tocantins (UFT), Palmas, Brazil
29 Researcher, Brasília, Brazil
30 Laboratório de Ecologia de Peixes, Departamento de Ecologia,
Universidade do Estado do Rio de Janeiro (UERJ), Rio de
Janeiro, Brazil
Environmental Management
31 Laboratório de Análise e Síntese em Biodiversidade,
Departamento de Botânica, Universidade Federal do Paraná
(UFPR), Curitiba, Brazil
32 Secretaria de Estado da Educação de Goiás-(Seduc-GO),
Luziânia, Goiás, Brazil
33 UNISANTA, PPGECOMAR, Santos, Brazil
34 Universidade Federal do Tocantins (UFT), Porto Nacional, Brazil
35 Laboratório de Paleobiologia, Universidade Federal do Tocantins
(UFT), Porto Nacional, Brazil
36 Departamento de Ecologia e Conservação, Universidade Federal
de Lavras (UFLA), Lavras, Brazil
37 Laboratório de Caracterização de Impactos Ambientais (LCIA),
Universidade Federal do Tocantins (UFT), Palmas, Brazil
38 Embrapa Cerrado, Planaltina, Brazil
39 Instituto de Biodiversidade e Sustentabilidade, Universidade
Federal do Rio de Janeiro, Macaé, Brazil
40 Programa de Pós-Graduação em Ecologia, Universidade Federal
do Pará (UFPA), Belém, Brazil
41 Laboratório de Análises Geoambientais (LGA), Universidade
Federal do Tocantins (UFT), Porto Nacional, Brazil
42 Centro de Biologia Aquática, Pontifícia Universidade Católica de
Goiás, Goiânia, Brazil
43 Laboratório de Biodiversidade, Universidade Evangélica de Goiás,
Anápolis, Brazil
44 Escola de Ciências Agrárias e Biológicas, Pontifícia Universidade
Católica (PUC), Goiânia, Brazil
45 Laboratório de Genética & Biodiversidade - ICB/UFG,
Goiânia, Brazil
46 Núcleo de Pesquisas em Limnologia, Ictiologia e Aquicultura
(Nupelia), Universidade Estadual de Maringá (UEM),
Maringá, Brazil
47 Departamento de Direito, Universidade Federal do Tocantins
(UFT), Palmas, Brazil
48 Núcleo de Estudos e Pesquisas Ambientais e Limnológicas
(Nepal), Universidade de Brasília (UnB), Planaltina-DF, Brazil
49 Laboratório de Ecologia e Conservação (LEC), Universidade
Federal do Paraná (UFPR), Curitiba, Brazil
50 Coordenação de Biodiversidade, Instituto Nacional de Pesquisas
da Amazônia (INPA), Manaus, Brazil
Environmental Management
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