ArticlePDF Available

Environmental Management Large-scale Degradation of the Tocantins-Araguaia River Basin

Authors:

Abstract and Figures

The Tocantins-Araguaia Basin is one of the largest river systems 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.
This content is subject to copyright. Terms and conditions apply.
Environmental Management
https://doi.org/10.1007/s00267-021-01513-7
Large-scale Degradation of the Tocantins-Araguaia River Basin
Fernando Mayer Pelicice 1Angelo Antonio Agostinho2Alberto Akama3José Dilermando Andrade Filho4
Valter M. Azevedo-Santos5Marcus Vinicius Moreira Barbosa6Luis Mauricio Bini7
Marcelo Fulgêncio Guedes Brito8Carlos Roberto dos Anjos Candeiro9Érica 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 Filho7Philip 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.7Pedro 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 Shimabukuro4Idelina 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 basins
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 sh. 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 basins 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 oodplains in
the world (Latrubesse et al. 2019). The Araguaia River is
also one of the few large free-owing 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.
1234567890();,:
1234567890();,:
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 conicts. 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
signicant 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
sh 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 sh 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 connement 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 rst 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 shes
(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 catsh
(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 sh 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 sh in the Tocantins-Araguaia Basin.
This episode illustrates how government policies, guided
by short-term economic prots, ignore scientic 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 catsh (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 sh 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 sh 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 shes.
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 scientic
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-
tic 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 ow regimes of
remaining free-owing 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 conicts 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 Cientíco e Tecnológico (CNPq) provided research
grants.
Author Contributions FMP conceived the idea and wrote the rst
draft. All authors contributed with writing, development, and revision.
Funding Some authors have been supported by different agencies,
especially Conselho Nacional de Desenvolvimento Cientíco e Tec-
nológico (CNPq) and Coordenação de Aperfeiçoamento de Pessoal de
Nível Superior (Capes).
Environmental Management
Compliance with Ethical Standards
Conict 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.
Publishers note Springer Nature remains neutral with regard to
jurisdictional claims in published maps and institutional afliations.
References
Agostinho AA, Gomes LC, Pelicice FM (2007) Ecologia e manejo de
recursos pesqueiros em reservatórios do Brasil. Eduem, Maringá,
p 501
Akama A (2017) Impacts of the hydroelectric power generation over
the sh fauna of the Tocantins river, Brazil: Marabá Dam, the
nal blow. Oecologia Aust 21(3):222231. https://doi.org/10.
4257/oeco.2017.2103.01
Araújo ES, Marques EE, Freitas IS, Neuberger AL, Fernandes R,
Pelicice FM (2013) Changes in distance decay relationships after
river regulation: similarity among sh assemblages in a large
Amazonian river. Ecol Freshw Fish 22:543552
Azevedo-Santos VM, Rigolin-Sá O, Pelicice FM (2011) Growing,
losing or introducing? Cage aquaculture as a vector for the
introduction of non-native sh in Furnas Reservoir, Minas Gerais,
Brazil. Neotrop Ichthyol 9:915919
Azevedo-Santos VM, Frederico RG, Fagundes CK, Pompeu PS,
Pelicice FM, Padial AA, Nogueira MG, Fearnside PM, Lima LB,
Daga VS, Oliveira FJM, Vitule JRS, Callisto M, Agostinho AA,
Esteves FA, Lima-Junior DP, Magalhães ALB, Sabino J, Mormul
RP, Grasel D, Zuanon J, Vilella FS, Henry R (2019) Protected
areas: a focus on Brazilian freshwater biodiversity. Divers Distrib
25:442448. https://doi.org/10.1111/ddi.12871
Azevedo-Santos VM, Rodrigues-Filho JL, Fearnside PM, Lovejoy TE,
Brito MFG (2021) Conservation of Brazilian freshwater biodi-
versity: Thinking about the next 10 years and beyond. Biodivers
Conserv 30:235241. https://doi.org/10.1007/s10531-020-02076-5
Bezerra LAV, Freitas MO, Daga VS, Occhi TVT, Faria L, Costa APL,
Padial AA, Prodocimo V, Vitule JRS (2019) A network meta-
analysis of threats to South American sh biodiversity. Fish Fish
20:620639. https://doi.org/10.1111/faf.12365
Burger JR, Allen CD, Brown JH, Burnside WR, Davidson AD, Fristoe
TS, Hamilton MJ, Mercado-Silva N, Nekola JC, Okie JG, Zuo W
(2012) The macroecology of sustainability. PLoS Biol 10(6):
e1001345. https://doi.org/10.1371/journal.pbio.1001345
Canonico GC, Arthington A, McCrary JK, Thieme ML (2005) The
effects of introduced tilapias on native biodiversity. Aquat Con-
serv 15:463483. https://doi.org/10.1002/aqc.699
Carolina RdC, Doria E, Agudelo A, Akama B, Barros M, BonmL,
Carneiro SR, Briglia-Ferreira L, Nobre CCA, Bonilla-Castillo P,
Charvet DTB, dosSantos CHP, da Silva CR, Garcia-Dávila HDB,
dos AF, Duponchelle A, Encalada I, Fernandes AC, Florentino
PCP, Guarido TL, de Oliveira G, Jimenez-Segura OM, Lasso-
Alcalá MR, Macean EE, Marques RNG, Mendes-Júnior G,
Miranda-Chumacero JLS, Nunes TVT, Occhi LS, Pereira W,
Castro-Pulido L, Soares RGC, Sousa G, Torrente-Vilara PA, Van
DJ, Zuanon JR Simões, Vitule (2021) The Silent Threat of Non-
native Fish in the Amazon: ANNF Database and Review. Front in
Eco and Evol 9. https://doi.org/10.3389/fevo.2021.646702
Carvalho RA, Tejerina-Garro FL (2019) Spatial and temporal trends in
freshwater sh research: the case of three neotropical river basins
from Goiás State, Central Brazil. Acta Limnol Bras 31:e25.
https://doi.org/10.1590/S2179-975X5418
Coe MT, Brando PM, Deegan LA, Macedo MN, Neill C, Silvério DV
(2017) The forests of the Amazon and Cerrado moderate regional
climate and are the key to the future. Trop Conserv Sci 10:16.
https://doi.org/10.1177/1940082917720671
Coe MT, Costa MH, Soares-Filho BS (2009) The inuence of his-
torical and potential future deforestation on the stream ow of the
Amazon River-Land surface processes and atmospheric feed-
backs. J Hydrol 369:165174. https://doi.org/10.1016/j.jhydrol.
2009.02.043
Colli GR, Vieira CR, Dianese JC (2020) Biodiversity and conservation of
the Cerrado: recent advances and old challenges. Biodivers Conserv
29:14651475. https://doi.org/10.1007/s10531-020-01967-x
Daga VS, Azevedo-Santos VM, Pelicice FM, Fearnside PM, Perbiche-
Neves G, Paschoal LRP, Cavallari DC, Erickson J, Ruocco
AMC, Oliveira I, Padial AA, Vitule JRS (2020) Water diversion
in Brazil threatens biodiversity. Ambio 49:165172. https://doi.
org/10.1007/s13280-019-01189-8
Dagosta FCP, de Pinna M (2019) The shes of the Amazon: dis-
tribution and biogeographical patterns, with a comprehensive list
of species. Bull Am Mus Nat Hist 431:1163. https://doi.org/10.
1206/0003-0090.431
De Sousa PT, Piedade MTF, Candotti E (2011) Ecological oversight:
Brazils forest code puts wetlands at risk. Nature 478:458. https://
doi.org/10.1038/478458b
Diana JS (2009) Aquaculture production and biodiversity conservation.
BioScience 59:2738. https://doi.org/10.1525/bio.2009.59.1.7
Dobrovolski R, Loyola R, Rattis L, Gouveia SF, Cardoso D, Santos-
Silva R, Gonçalves-Souza D, Bini LM, Diniz-Filho JAF (2018)
Science and democracy must orientate Brazils path to sustain-
ability. Perspect Ecol Conserv 16:121124. https://doi.org/10.
1016/j.pecon.2018.06.005
Doria CRC, Athayde S, Marques EE, Lima MAL, Dutka-Gianelli J,
Rufno ML, Kaplan D, Freitas CEC, IsaacVN (2017) The invi-
sibility of sheries in the process of hydropower development
across the Amazon. Ambio 47(4):453465. https://doi.org/10.
1007/s13280-017-0994-7
Fearnside PM (2001) Environmental impacts of Brazils Tucuruí
Dam: Unlearned lessons for hydroelectric development in
Amazonia. Environ Manag 27(3):377396. https://doi.org/10.
1007/s002670010156
Fearnside PM (2016) Brazilian politics threaten environmental policies.
Science 353:746748. https://doi.org/10.1126/science.aag0254
Ferrante L, Fearnside FM (2019) Brazils new president and ruralists
threaten Amazonias environment, traditional peoples and the
global climate. Environ Conserv 46:261663. https://doi.org/10.
1017/S0376892919000213
Forneck SC, Dutra FM, Camargo MP, Vitule JRS, Cunico AM (2021)
Aquaculture facilities drive the introduction and establishment of
non-native Oreochromis niloticus populations in Neotropical
streams. Hydrobiologia 848:19551966. https://doi.org/10.1007/
s10750-020-04430-8
Garcia DAZ, Magalhães ALB, Vitule JRS, Casimiro ACR, Lima-Junior
DP, Cunico AM, Brito MFG, Petrere-Junior M, Agostinho AA, Orsi
ML (2018) The same old mistakes in aquaculture: the newlyavailable
striped catsh Pangasianodon hypophthalmus is on its way to put-
ting Brazilian freshwater ecosystems at risk. Biodivers Conserv
27:35453558. https://doi.org/10.1007/s10531-018-1603-1
ICMBio (Instituto Chico Mendes de Conservação da Biodiversidade)
(2018) Livro Vermelho da Fauna Brasileira Ameaçada de Extinção:
Volume VI - Peixes. ICMBio, Brasília, DF, Brazil
Latrubesse E, Arima E, Dunne T, Park E, Baker V, Horta F, Wight C,
Wittmann F, Zuanon J, Baker P, Ribas C, Norgaard R, Filizola N,
Environmental Management
Ansar A, Flyvbjerg B, Stevaux J (2017) Damming the rivers of
the Amazon basin. Nature 546:363369. https://doi.org/10.1038/
nature22333
Latrubesse EM, Arima E, Ferreira ME, Nogueira SH, Wittmann F,
Dias MS, Dagosta FCP, Bayer M (2019) Fostering water resource
governance and conservation in the Brazilian Cerrado biome.
Conserv Sci Pract 1:e77. https://doi.org/10.1111/csp2.77
Lima LB, Oliveira FJ, Giacomini HC, Lima Jr DP (2018) Expansion
of aquaculture parks and the increasing risk of non-native species
invasions in Brazil. Rev Aquacult 10:111122. https://doi.org/10.
1111/raq.12150
Lima Jr DP, Magalhães ALB, Pelicice FM, Vitule JRS, Azevedo-
Santos VM, Orsi ML, Simberloff D, Agostinho AA (2018)
Aquaculture expansion in Brazilian freshwaters against the Aichi
biodiversity targets. Ambio 47:427440. https://doi.org/10.1007/
s13280-017-1001-z
Lopes GR, Lima MGB, Reis TNP (2021) Maldevelopment revisited:
inclusiveness and social impacts of soy bean expansion over
Brazils Cerrado in Matopiba. World Dev 139:105316. https://
doi.org/10.1016/j.worlddev.2020.105316
Lopes RF, Candeiro CRA, de Valais S (2019) Geoconservation of the
paleontological heritage of the geosite of dinosaur footprints
(sauropods) in the locality of São Domingos, municipality of
Itaguatins, state of Tocantins, Brazil. Environ Earth Sci 78:707.
https://doi.org/10.1007/s12665-019-8722-1
Lucinda PHF, Freitas IS, Soares AB, Marques EE, Agostinho CS,
Oliveira RJ (2007) Fish, Lajeado Reservoir, rio Tocantins drai-
nage, State of Tocantins, Brazil. Check List 3:7083. https://doi.
org/10.15560/3.2.70
Machado KB, Targueta CP, Antunes AM, Soares TN, Telles MPC,
Logares R, Vieira LCG, Huszar VLM, Nabout JC (2019) Diversity
patterns of planktonic microeukaryote communities in tropical
oodplain lakes based on 18S rDNA gene sequences. J Plankton Res
41(3):241256. https://doi.org/10.1093/plankt/fbz019
MapBiomas, 2021. Collection 5 of Brazilian Land Cover & Use Map
Series. https://mapbiomas.org/download (Accessed March 2021).
Martinelli LA, Naylor R, Vitousek PM, Moutinho P (2010) Agri-
culture in Brazil: impacts, costs, and opportunities for a sustain-
able future. Curr Opin Environ Sustain 2:431438. https://doi.
org/10.1016/j.cosust.2010.09.008
Martins PR, Sano EE, Martins ES, Vieira LCG, Salemi LF, Vasconcelos
V, Couto Júnior AF (2021) Terrain units, land use and land cover,
and gross primary productivity of the largest uvial basin in the
Brazilian Amazonia/Cerrado ecotone: the Araguaia River basin. Appl
Geogr 127:102379. https://doi.org/10.1016/j.apgeog.2020.102379
Morais PB, Noleto Jr S, Martins ICM (2014) Análise de sustentabil-
idade do projeto hidroagrícola Javaés/LAGOA, no estado do
Tocantins. Cad de Ciência Tecnologia 34(1):83111. https://doi.
org/10.35977/0104-1096.cct2017.v34.26297
Nepstad D, Mcgrath D, Stickler C, Alencar A, Azevedo A, Swette B,
Bezerra T, DiGiano M, Shimada J, Motta RS, Armijo E, Castello L,
Brando P, Hansen MC, MsGrath-Horn M, Carvalho O, Hess L
(2014) Slowing Amazon deforestation through public policy and
interventions in beef and soy supply chains. Science 344:11181123.
https://doi.org/10.1126/science.1248525
Pelicice FM, Castello L (2021). A political tsunami hits Amazon con-
servation. Aquatic Conserv Mar Freshw Ecosyst. 31:12211229.
https://doi.org/10.1002/aqc.3565
Pelicice FM, Azevedo-Santos VM, Vitule JRS, Orsi ML, Lima Jr DP,
Magalhães ALB, Pompeu PS, Petrere Jr M, Agostinho AA (2017)
Neotropical freshwater shes imperiled by unsustainable policies.
Fish Fish 18:11191133. https://doi.org/10.1111/faf.12228
Pelicice FM, Vitule JRS, Lima Jr DP, Orsi ML, Agostinho AA (2014)
A serious new threat to Brazilian freshwater ecosystems: the
naturalization of nonnative sh by decree. Conserv Lett 7:5560.
https://doi.org/10.1111/conl.12029
Pereira HR, Gomes LR, Soares PT, Martins PR, Pelicice FM, Teresa
FB, Vieira LCG (2021) Long-term responses of sh diversity to
river regulation: a multi-metric approach. Environ Biol Fish
104:7184. https://doi.org/10.1007/s10641-021-01056-0
Perônico PB, Agostinho CS, Fernandes R, Pelicice FM (2020) Com-
munity reassembly after river regulation: rapid loss of sh
diversity and the emergence of a new state. Hydrobiologia 847
(2):519533. https://doi.org/10.1007/s10750-019-04117-9
Ribeiro MCLB, Petrere Jr M, Juras AA (1995) Ecological integrity
and sheries ecology of the AraguaiaTocantins River basin,
Brazil. Regul Rivers: Res Manag 11(34):325350. https://doi.
org/10.1002/rrr.3450110308
Salvador GN, Leal CG, Brejão GL, Pessali TC, Alves CBM, Rosa GR,
Ligeiro R, Montag LFA (2020) Mining activity in Brazil and
negligence in action. Perspect Ecol Conserv 18:139144. https://
doi.org/10.1016/j.pecon.2020.05.003
Santana MLC, Carvalho FR, Teresa FB (2021) Broad and ne-scale
threats on threatened Brazilian freshwater sh: variability across
hydrographic regions and taxonomic groups. Biota Neotropica 21(2):
e20200980. https://doi.org/10.1590/1676-0611-BN-2020-0980
Scaramuzza CAM, Sano EE, Adami M, Bolfe EL, Coutinho AC
(2017) Land-use and Land-cover mapping of the Brazilian Cer-
rado based mainly on Landsat-8 satellite images. Rev Bras Car-
tograa 69(6):10411051. 2017
Strassburg BBN, Brooks T, Feltran-Barbieri R, Iribarrem A, Crou-
zeilles R, Loyola R, Latawiec AE, Oliveira FJB, Scaramuzza
CAD, Scarano FR, Soares B, Balmford A (2017) Moment of
truth for the Cerrado hotspot. Nat Ecol Evol 1:3. 10.1038/s4155
9-017-0099
Swanson AC, Bohlman S (2021) Cumulative impacts of land cover
change and dams on the landwater interface of the Tocantins
River. Front Environ Sci 9:662904. https://doi.org/10.3389/fenvs.
2021.662904
Thomaz SM, Gomes Barbosa L, de Souza Duarte MC, Panosso R
(2020) The future of nature conservation in Brazil. Inland Waters
10:295303. https://doi.org/10.1080/20442041.2020.1750255
Trigueiro WR, Nabout JC, Tessarolo G (2020) Uncovering the spatial
variability of recent deforestation drivers in the Brazilian Cerrado.
J Environ Manag 275:111243. https://doi.org/10.1016/j.jenvman.
2020.111243
Vitule JRS (2009) Introdução de peixes em ecossistemas continentais
brasileiros: revisão, comentários e sugestões de ações contra o
inimigo quase invisível. Neotrop Biol Conserv 4:111122.
https://doi.org/10.4013/5123
Vitule JRS, Freire CA, Simberloff D (2009) Introduction of non-native
freshwater sh can certainly be bad. Fish Fish 10:98108. https://
doi.org/10.1111/j.1467-2979.2008.00312.x
Winemiller KO, McIntyre PB, Castello L, Fluet-Chouinard E, Giar-
rizzo T, Nam S, Baird IG, Darwall W, Lujan NK, Harrison I,
Stiassny MLJ, Silvano RAM, Fitzgerald DB, Pelicice FM,
Agostinho AA, Gomes LC, Albert JS, Baran E, Petrere Jr M,
ZarC, Mulligan M, Sullivan JP, Arantes CC, Sousa LM,
Koning AA, Hoeinghaus DJ, Sabaj M, Lundberg JG, Armbruster
J, Thieme ML, Petry P, Zuanon J, Torrente Vilara G, Snoeks J,
Ou C, Rainboth W, Pavanelli CS, Akama A, van Soesbergen A,
Sáenz L (2016) Balancing hydropower and biodiversity in the
Amazon, Congo, and Mekong. Science 351:128129. https://doi.
org/10.1126/science.aac7082
Environmental Management
Afliations
Fernando Mayer Pelicice 1Angelo Antonio Agostinho2Alberto Akama3José Dilermando Andrade Filho4
Valter M. Azevedo-Santos5Marcus Vinicius Moreira Barbosa6Luis Mauricio Bini7
Marcelo Fulgêncio Guedes Brito8Carlos Roberto dos Anjos Candeiro9Érica 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 Filho7Philip 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.7Pedro 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 Shimabukuro4Idelina 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 Biogeograa 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
... The Tocantins-Araguaia basin is currently the most targeted area for expanding agricultural activities, as stated in Presidential Decree 8447 of 2015, which created the MATOPIBA Federal Plan for the Development of the Brazilian Cerrado. Data from 2019 indicate that pastures and monocultures covered more than 42% of the basin [33]. Agricultural expansion has dramatically increased the use of pesticides [40,41], which invariably end up in aquatic ecosystems. ...
... These activities result in numerous discharges being emitted into the atmosphere and the aquatic system, causing harm to the health of the Tocantins River (both fauna and flora) and impacting the quality of life of the population dependent on the river. Threats are escalating as public policies continue to prioritize maximizing economic growth at the cost of environmental sustainability [33]. Fishing is a cultural activity that has been generating income for generations in the region [45]. ...
... The Tocantins-Araguaia region 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) [33]. Continuous monitoring of this water resource is essential for addressing and mitigating water pollution, as contaminated water poses serious health risks to human and animal health. ...
Article
Full-text available
The Tocantins–Araguaia basin is one of South America’s largest river systems, across three Brazilian states (Maranhão, Tocantins, and Pará), within the Legal Amazon region. Despite draining extensive Cerrado savanna and rainforest ecosystems, it has suffered significant degradation, notably in the past 40 years. Human activities, including agricultural expansion, deforestation, and the introduction of non-native species, have worsened the environmental damage, which is alarming since many residents and villages along the middle Tocantins River rely on it for water supply, recreation, and fishing. This study assessed the concentration of potentially toxic and essential elements in water samples from four sampling sites distributed along the middle Tocantins River. The monitoring occurred throughout 2023, involving the measurement of parameters both on-site and in the laboratory. Water quality and its health implications were evaluated using the Weighted Arithmetic Water Quality Index (WAWQI), the Water Quality Index (WQI), and the health risk assessment index. The levels of aluminum, copper, iron, magnesium, and selenium exceeded legal standards. Seasonal fluctuations indicate a complex dynamic influenced by climatic or seasonal factors, with February showing the highest values. Site P1, located in urban areas, exhibited elevated mean concentrations for conductivity, total dissolved solids (TDS), and chlorophyll, indicating the need for continuous monitoring. The nitrogen concentrations at P1 raise concerns regarding drinking water quality, which is a concern for the region’s residents who use untreated river water. Despite seasonal variations in element concentrations, the overall WAWQI categorized all sections as “Excellent,” and the WQI rated as “Good.” Human health risk assessments detected no risks, but continuous monitoring and interventions are crucial for sustained water quality improvement.
... Pseudopaludicola jazmynmcdonaldae was the most recently described among these species and remains restricted to its type locality, namely, Caseara Municipality, western Tocantins State (Andrade et al., 2019). This municipality is in the Araguaia-Tocantins interfluve; it is one of the largest drainage systems of Brazil that is severely affected by agribusiness, mining, and hydropower activities (Bezerra and Gonzaga, 2019;Pelicice et al., 2021). Western Tocantins State is more influenced by the Araguaia River and its main tributaries (e.g., the Coco, Riozinho, Formoso, and Javaés rivers), a drainage system characterized by extensive floodplains, including both seasonally flooded forests (''igapós'') and grasslands. ...
... The most direct consequence of this expansion is the loss of natural areas and soil degradation. Indeed, between 2002 and 2013, Tocantins experienced an astonishing increase of 328% in cropland area and 29% in pastureland Pelicice et al., 2021). The Araguaia-Tocantins interfluve corresponds to 1 of 10 mesoregions of Matopiba (Occidental Tocantins), where the production of soy has consistently increased, with Lagoa da Confusão, Pium, Marianópolis, and Caseara municipalities as highlights in soy expansion (Araújo et al., 2019). ...
... The Araguaia-Tocantins interfluve corresponds to 1 of 10 mesoregions of Matopiba (Occidental Tocantins), where the production of soy has consistently increased, with Lagoa da Confusão, Pium, Marianópolis, and Caseara municipalities as highlights in soy expansion (Araújo et al., 2019). In fact, the current level of anthropization of the Araguaia-Tocantins River basin requires urgent attention from conservation managers to safeguard the singular biodiversity of this region (Pelicice et al., 2021). Such high rates of habitat loss become more dramatic when we consider the high levels of biodiversity underestimation of the Neotropical Region and that many of the recently described and undescribed species already face extinction risk with few public policies to protect them (Fiser et al., 2018;Liu et al., 2022). ...
... Loss of habitat, pollution, alteration of water flow and the presence of non-native species are among the disturbances that threaten freshwater biodiversity around the world (Collen et al., 2014). Currently, all these disturbances are affecting freshwater biodiversity of Brazilian watersheds (Azevedo-Santos et al., 2019;Pelicice et al., 2021;Coelho et al., 2023). ...
Article
Serrasalmus brandtii is native from the São Francisco River Basin. However, this species has been introduced in numerous other watersheds. Here we report the first occurrences of S. brandtii and its dispersal in the Doce River Basin, in southeastern Brazil. In addition, we discuss the possible impacts of the species on native fish assemblages of this region. The individuals were captured during four years of aquatic biodiversity monitoring (2018–2022) after the Fundão mining ore tailing collapse in 2015. Data from SpeciesLink and literature were used to complement the dispersal history in the Doce River Basin. Our results show that the species occurred in nine localities in the lower portion of the watershed. The first record occurred in 1987, in the Santa Maria do Doce River, in the State of Espírito Santo, Brazil. The establishment of S. brandtii in the watershed poses a real threat to native species, aggravating the effects of other anthropogenic impacts.
... However, these same characteristics are of interest to the Sustainability 2024, 16, 2303 4 of 21 electric sector, with several projects operating in the basin. According to [11] (2021), this and other anthropogenic activities have resulted in the large-scale degradation of the basin. ...
Article
Full-text available
The management of water resources is a complex issue, and the conservation of fish and fishery resources is a growing challenge given the increase in the number of hydroelectric projects in Brazilian river basins. This study describes the fragmentation of the Tocantins–Araguaia River Basin resulting from the installation of hydroelectric plants in operation and planned by the electricity sector until 2050, as well as its relationship with the conservation of fish fauna, especially long-distance migratory species. The hydroelectric projects in operation and planned were analyzed using data obtained from the National Electric Energy Agency. A literature review was carried out to assess the fish species of the Tocantins–Araguaia ecoregion, with an emphasis on long-distance migrants. In general, 75 hydroelectric dams are in operation, and a further 119 projects are in the electricity sector’s plans for construction by 2050 in the Tocantins–Araguaia ecoregion, including a stretch of the basin above the Tucurui dam, which will accentuate the fragmentation in the area. Of the 702 species found in the region, 31.1% are endemic, 6.1% are endangered, and several long-distance migratory species have had their populations restricted. Analysis of this information highlights the widespread impact on the ichthyofauna, affecting both species with a restricted distribution and migratory species with a long-distance distribution. The studies associated with the projects contribute to the advancement of knowledge, but they are only carried out after the works have been defined, which makes it difficult to plan conservation in advance. Transformations in the basin are imminent given the current changes and those expected in the coming years because of the electricity sector’s planning for the region. Considering the inseparable relationship between biodiversity and socio-environmental and cultural diversity, fish conservation is intrinsically linked to the conservation of socio-diversity and the effective participation of local communities from the start of the process. Fish depend on water, and people need both water and aquatic diversity. In conclusion, a well-structured and adaptative conservation plan, combined with the integration of effective fish routes, can contribute to the sustainable development of hydroelectric projects while safeguarding the biodiversity and ecological integrity of the Tocantins–Araguaia Basin.
... Agriculture activities have generated negative impacts on Brazilian environments and biodiversity (Hepp et al., 2010;Pelicice et al., 2021). In the last 50 years, the irrigated area in Brazil increased by approximately a factor of 10, and in 2015, this area totaled~7 million hectares, with projections indicating it would reach 10 million hectares by 2030 (ANA, 2019). ...
Article
Full-text available
Brazil is among the main contributors to global biodiversity, which, in turn, provides extensive ecosystem services. Agriculture is an activity that benefits greatly from these ecosystem services, but at the same time is degrading aquatic and terrestrial ecosystems and eroding Brazilian biodiversity. This conflict is growing, as emerging unsustainable legislative proposals that will benefit the agricultural sector are likely to accelerate the decline of biodiversity. One such initiative (Bill 1282/2019) would change Brazil’s “Forest Code” (Law 12,651/2012) to facilitate construction of irrigation dams in Permanent Preservation Areas, a category that includes strips (with or without vegetation) along the edges of watercourses. Two other similar bills are advancing through committees in the Chamber of Deputies. Here we provide details of these three bills and discuss their consequences for Brazil’s biodiversity if they are approved. Expected negative impacts with changes in the legislation include: increased deforestation; siltation; habitat fragmentation; introduction of non-native species; reduction in the availability of aquatic habitats; and changes in biogeochemical process. These proposals jeopardize biodiversity and may compromise the negotiations for an agreement between Mercosur and the European Union.
... The rapid conversion, coupled with high species richness and endemism, classifies the Cerrado biome as a biodiversity hotspot (Myers et al., 2000). The Tocantins-Araguaia basin, primarily located within the Cerrado biome, has been experiencing large-scale degradation (Pelicice et al., 2021). In particular, the Araguaia River basin is the main drainage artery of the Cerrado biome, including the largest and most important wetland areas in Central Brazil, including a Ramsar site (MMA, 2022). ...
Article
Full-text available
Freshwater aquatic ecosystems are vulnerable to human activities within their surroundings, presenting a concerning scenario for aquatic organisms and human subsistence. Therefore, understanding the occurrence of pesticide contamination is a necessary condition to safeguard aquatic biodiversity and human health. We analysed the pesticide residues in water samples, using the solid-phase extraction (SPE) technique and determination by ultra performance liquid chromatography coupled with tandem mass spectrometry (UPLC‒MS/MS). We also we investigated whether land use influences water contamination by pesticides in the middle and upper Araguaia River basin, situated in the central region of Brazil in the Cerrado biome. We evaluated the effect of land use and land cover type on pesticide occurrence in nine subbasins using mixed linear models. We registered the occurrence of pesticides in all subbasins. After water analysis a total of eight pesticides were found: atrazine, carbendazim, cyanazine, imidacloprid, 2,4-D, clomazone, chlorpyrifos-ethyl, and imazalil. Atrazine and carbendazim were detected during both sampling years. The active ingredient atrazine and clomazone were registered in all studied subbasins, with concentrations ranged from 0.006–0.207 µg L−1 and 0.183–0.373 µg L−1, respectively. There were no significant relationships observed between the number of pesticides and the type of land use and land cover, a result possibly related to the short sampling period, as these pesticides are largely used for fungi and insect control in agricultural areas. The presence of pesticides in the water may have potentially detrimental effects on aquatic biodiversity because sampled pesticides have been associated with anomalies in ontogenetic development, diseases, and mortality in organisms. Based on European legislation, it was evident that most of the subbasins had pesticide concentrations in the water exceeding the safety levels for human consumption. Thus, it is crucial for Brazilian legislation to establish maximum limits for pesticide concentrations in water to ensure safe drinking water for the Brazilian population. Additionally, a permanent monitoring system should be established to understand contamination trends in this basin and to take appropriate actions to mitigate adverse impacts.
... Hydrobiologia commodities, resulting in increased water extraction from the watershed to support these activities (Latrubesse et al., 2019;Pelicice et al., 2021). Consequently, both water surface area and water flow in the Araguaia River basin have experienced significant reductions over the years, which aligns with findings from previous studies conducted in the basin (Rosin et al., 2015;Lima et al., 2022). ...
Article
Full-text available
Reconciling environmental conservation with growing demands for food, water, and energy is a global challenge. Brazil, a major agricultural producer, grapples with deforestation’s environmental costs. The Araguaia River basin, vital for Brazil’s economic growth, undergoes significant land use changes. Assessing data from 1987 to 2019, we studied annual water surface variations, considering deforestation, agriculture, livestock farming land, and central pivot irrigation, and historical water flow series from 1980 to 2020 from 21 monitoring stations. We observed notable reductions in flooded areas (angular coefficients from 130 a 2,276 ha/year) and water flow the entire basin (b = − 13.84; t = − 4.8; P < 0.001) and its regions (Upper Araguaia: b = − 3.32; t = − 4.5; P < 0.001; Middle Araguaia: b = − 8.70; t = − 4.8; P < 0.001; Lower Araguaia: b = − 45.49, t = − 4.7; P < 0.001) over recent years. Water flow reductions persist year-round, with a marked decrease during low water periods (F3,8 = 8.82; P = 0,006), aligning with heightened water demand for intensive agriculture. Tributaries and the main channel show similar reduction processes (t = 0.16; g.l. = 19; P = 0.873). Ensuring the basin’s ecological flow is imperative for the aquatic ecosystem’s minimum requirements.
... Rivers are influenced by several external factors, which individually or collectively can cause gradual or pulsating imbalances in their systems, mainly affecting their morphology ( The changes in two-dimensional morphology in multichannel river systems, which typically characterize the world's largest rivers, are conventionally conlateralred unpredictable using approaches developed for small rivers , featuring a complex network of channels generated during the Middle and Late Pleistocene by a multi-channel system (VALENTE; LATRUBESSE, 2012). Delineated by the Araguaia River on the left and the Javaés River on the right, the island is a unique system in the Cerrado biome in transition with the Amazon biome, which is still free from major direct alterations to the channel, such as the construction of dams (MARTINS et al., 2021;PELICICE et al., 2021). The current position of much of the Javaés River corresponds to an alluvial channel belt abandoned by the Araguaia River due to regional avulsion (IRION et al., 2016;LATRUBESSE, 2012). ...
Article
Full-text available
Bananal Island is the largest river island in the world, located in the Araguaia River basin in central-western Brazil. Studies on the Araguaia River have shown that changes in the main channel are linked to the increase in sediment input due to agricultural expansion in the Cerrado. However, very little is known about the Javaés River, on the opposite margin of Bananal Island. This study analyzed the temporal trends of sand bars and water masses in the Javaés River from 1985 to 2021. Annual mosaics of Landsat images were generated to identify the classes of water masses and sand bars. The Mann Kendall and Sen's Slope tests were used to identify trends and statistical significance of changes over time. The results indicated an increase of 57% (6.5 km²) in the areas of sand bars and a reduction of 39% (15.2 km²) in water bodies. The tests revealed significant trends with an increase in bars and a decrease in water bodies. It was observed that changes in the distribution and rates of regional precipitation, along with the expansion of anthropogenic occupation, are contributing to an increase in sediment input, in a cascade effect, affecting the balance between erosion and deposition in the Javaés River.
Article
Full-text available
Non-native fish (NNF) can threaten megadiverse aquatic ecosystems throughout the planet, but limited information is available for the Amazon Region. In this study we review NNF data in the Amazonian macroregion using spatiotemporal records on the occurrence and the richness of NNF from a collaborative network of 35 regional experts, establishing the Amazon NNF database (ANNF). The NNF species richness was analyzed by river basin and by country, as well as the policies for each geopolitical division for the Amazon. The analysis included six countries (Brazil, Peru, Bolivia, Ecuador, Venezuela, and Colombia), together comprising more than 80% of the Amazon Region. A total of 1314 NNF occurrence records were gathered. The first record of NNF in this region was in 1939 and there has been a marked increase in the last 20 years (2000–2020), during which 75% of the records were observed. The highest number of localities with NNF occurrence records was observed for Colombia, followed by Brazil and Bolivia. The NNF records include 9 orders, 17 families and 41 species. Most of the NNF species are also used in aquaculture (12 species) and in the aquarium trade (12 species). The most frequent NNF detected were Arapaima gigas, Poecilia reticulata and Oreochromis niloticus. The current data highlight that there are few documented cases on NNF in the Amazon, their negative impacts and management strategies adopted. The occurrence of NNF in the Amazon Region represents a threat to native biodiversity that has been increasing “silently” due to the difficulties of large-scale sampling and low number of NNF species reported when compared to other South American regions. The adoption of effective management measures by decision-makers is urgently needed and their enforcement needed to change this alarming trend and help protect the Amazon’s native fish diversity.
Article
Full-text available
Anthropogenic environmental changes are the main cause of species extinction during the Holocene. Species have been exposed to major source of threats, such as habitat loss and fragmentation, pollution, introduced species, and harvesting, many of which are derived from specific anthropogenic activities, such as urbanization, agriculture, and damming (i.e. fine-scale threats). However, the importance of these threats on the species conservation status in a given region depends on the type of impacts they are exposed to and the susceptibility of species to these impacts. In this study, we used a database of threatened Brazilian freshwater fish species to test whether the major source of threats and the specific anthropogenic impacts to species vary across hydrographic regions and taxonomic groups. Our results showed that habitat loss is a ubiquitous major threat jeopardizing the conservation status of the Brazilian fish species. However, different fine�scale threats mediate this process across hydrographic regions and taxonomic groups. The combination of impacts from agriculture, deforestation, and urbanization affects most of the threatened species in the basins of the Northeast, South, and Southeast, including the species of the most threatened order, the Cyprinodontiformes. Damming is the main human activity affecting threatened species of Siluriformes, Characiformes, Gymnotiformes, and Cichliformes, especially in northern basins (Amazon and Tocantins-Araguaia). Therefore, we found that specific fine-scale threats influencing threatened species vary across hydrographic regions and taxonomic groups, probably due to geographic variability in the incidence of human activities and differential niche requirements and vulnerability of species to these activities.
Article
Full-text available
Riparian vegetation performs important ecosystems services, improving water quality, mitigating erosion, and maintaining regional plant and animal biodiversity. Regular annual flooding maintains riparian forests through an intermediate disturbance regime. In response, seasonally flooded vegetation has developed adaptations for seed dispersal and gas transfer to survive and reproduce while undergoing periods of flooding. In the Amazon, a dam building boom threatens the integrity of riparian vegetation by moving riparian corridors into dry-adapted ecosystems and reducing downstream flooding of riparian areas. Additionally, the region is undergoing intense development pressure resulting in the conversion of native riparian vegetation into agriculture. In this study, we measure how the installation of six large dams on the Tocantins River, coupled with land cover change from native forest and savanna to cattle pasture, has changed the land–water interface of this region. Using land cover data provided by MapBiomas, we quantified land cover change from 1985 to 2018 and measured changes in the riparian areas of the still free-flowing areas of the Tocantins River, riparian areas surrounding reservoirs, and in-stream vegetation dynamics. We found that deforestation in the riparian areas of the Tocantins River downstream of the dams is occurring at a higher rate than deforestation in the watershed. Additionally, reservoir filling resulted in creating hundreds of square kilometers of new riparian areas, pushing the riparian zone away from forest-dominated ecosystems into savanna-dominated areas. The quantity of in-stream vegetation throughout the study was dynamic and initially increased after damming before declining for the last decade of the study. Changes to native land cover in riparian areas of the Tocantins River threaten the integrity of ecosystem services provided by riparian vegetation and are likely to lead to further degradation of these areas.
Article
Full-text available
Large dams disrupt river ecosystems, causing negative effects on fish assemblages. Few studies, however, have investigated how Neotropical fish diversity responds to river regulation in longer temporal scales. In this study, we used a multi-metric approach to investigated temporal changes in taxonomic and functional fish diversity over 15 years-period following the construction of a large dam in the Upper Tocantins River, Amazon. We analyzed biological and environmental data collected in the impounded area before (2000–2002) and after (2003–2014) river regulation. Diversity metrics responded differently to the impoundment. Some metrics were not affected, as they showed little variation over years, such as fish abundance, species, and trait richness. Other metrics changed significantly between periods, such as taxonomic composition, temporal beta diversity, and trait abundance. Species with traits that are sensitive to hydrological alterations declined in the impoundment, while sedentary species were favored. Assemblage trajectories were variable, but community structure developed into a different state in the impoundment. Landscape variables explained changes in fish dissimilarity over time. In general, our study supports the notion that fish diversity in Amazonian rivers is vulnerable to river damming, but also indicates that different metrics show particular responses to this disturbance.
Article
Full-text available
Cash crops such as soy, cocoa and oil palm have expanded at great speed in developing countries, often at the expense of customary landowners, traditional livelihoods, and biodiversity. These landscape transformations have global drivers, but they are often justified by a dominant rationale that they bring development to otherwise underprivileged regions. Such development claims, however, are either taken at face value or conflated with simplistic macroeconomic indicators that gloss over most social issues. Those claims may, therefore, hide severe inequities. To better analyze these phenomena, we revisit and conceptualize the notion of maldevelopment, here defined as inequitable and exclusive processes of change that deprive most local stakeholders of their social and material capabilities. Using an inclusiveness framework , we then conduct an in-depth analysis of soy expansion in the Matopiba region of Brazil's Cerrado. This rich biome with a mosaic of land uses forms an agriculture-savanna landscape that is rapidly giving way to soy monoculture-under the guise of development. Through fieldwork and primary data collection in 18 Matopiba municipalities, we have interviewed 62 stakeholders in that landscape transformation from different social groups. We assess how soy expansion has altered access and allocation patterns of key resources such as land and water, as well as participation in the local food systems and governance initiatives. When looking beyond general economic indicators, our findings expose a brutally exclusive process of environmental degradation and resource dispossession. Yet the stakeholders we interviewed do not want to simply be left undisturbed but to experience inclusive development instead, with participation in governance and support for bottom-up initiatives. We conclude that the frequently cited claim that industrial monocultures bring development to underserved regions deserves far greater scrutiny, and that inclusiveness in the design and execution of interventions is crucial for avoiding maldevelopment.
Article
Full-text available
This study investigated whether aquaculture facilities drive the introduction and establishment of the non-native Nile tilapia (Orechromis niloticus) in Neotropical streams, Brazil. Samples were taken from nine streams with different aquaculture occupation intensities (no, moderate, and intense) using the percentage of occupation of micro-watersheds by aquaculture ponds as a proxy for propagule pressure. The presence of aquaculture facilities and the percentage of aquaculture occupation were good predictors of the catch frequency and of densities of tilapias in the adjacent natural environment. In the streams under intense propagule pressure, females prevailed and high densities of young individuals comparing to adults were recorded. It suggests that the species was reproductively successful in the natural environment. In the streams under moderate propagule pressure, males prevailed, which indicates the likely capture of individuals escaped from aquaculture facilities. In general, our results show the positive influence of propagule pressure on the introduction and establishment of Nile tilapia in natural ecosystems, showing that aquaculture expansion of O. niloticus poses a threat to the conservation of aquatic biodiversity.
Article
Full-text available
In 2021 the countries of the world will discuss a framework under the Convention on Biological Diversity (CBD) for a new environmental agenda for the next 10 years (“post-2020”). Parties should consider Brazil to be a central nation in these discussions. The country holds a large freshwater biodiversity that needs to be conserved, but current policies imperil species and ecosystems. Here we present topics to guide other CBD parties in discussing with Brazil a better agenda to conserve freshwater biodiversity post-2020. These initiatives include: (1) a national plan to reduce threats, (2) restoration of freshwater ecosystems, (3) protected areas, (4) more investment in research, and (5) science communication. Brazil’s participation in these CBD negotiations is fundamental for a new agreement, but the country is under a presidential administration with little concern for the environment. While our suggestions are intended for participants in the CBD negotiations, they will also be relevant to other international actors in the coming years. Nations, international investors, private companies and NGOs around the world must therefore use their influence to press the current administration to protect the country’s environment, including its enormous freshwater biodiversity.
Article
• The history of conservation of the Amazon can be viewed as a war involving many battles with interests in agribusiness on one side and in biodiversity conservation and sustainability on the other side. Trends in large‐scale deforestation in the 1970s spurred a series of policies, stakeholder alliances and international and grass‐roots movements, which decades later led to the establishment of protected areas and interventions in soy and beef supply chains of agribusiness. Together, these advances epitomized a conservation framework for the Amazon, which at one point nearly curbed deforestation in the Brazilian Amazon, although it included very few protections for freshwater ecosystems. • While those conservation advances were taking place, however, a series of policy changes started to undermine them through expansions in deforestation, river regulation and mining activities. The election of Brazil's President Jair Bolsonaro in 2019 then hit the Amazon conservation framework much like a tsunami of policy setbacks and the re‐establishment of the economic policies that sparked the Amazon war in the past. • The current trajectory is one of large‐scale degradation of Amazonian ecosystems and biodiversity with consequent impacts on local people. Because freshwater ecosystems are highly sensitive to human activities on water and on land, these growing impacts are particularly large. • It is too early to know, but four decades of institutional and policy developments to conserve the Brazilian Amazon may soon be pushed past the point from which they will be able to recover. Four conditions will be pivotal to allowing the Amazon conservation framework to recoup: (a) the end of Bolsonaro’s mandate in 2022 or earlier; (b) remobilization of stakeholders; (c) investments in environmental research, policy and multiple collaborations; and (d) moving conservation beyond terrestrial landscapes to also encompass freshwater ecosystems and their people.
Article
Integrity of most of tropical wetlands is threatened because they are often considered freely available resources of land and water. The Bananal, in the Araguaia River Basin, and the Pantanal in the Paraguai River Basin, are the two largest Brazilian wetlands influenced by the tropical seasonal floods. The purpose of this study is to integrate landscape structural and functional factors with the GPP dynamics over different terrain units present in the Araguaia River Basin. The study was conducted through the integration of different databases, including the topographic domains, protected areas and indigenous lands; land use and land cover map (year 2016); time series of GPP derived from the Moderate Resolution Imaging Spectroradiometer (MODIS) sensor (period of 2000–2015); Shuttle Radar Topography Mission (SRTM) digital elevation models (DEM); and precipitation data produced by the WorldClim version 2 dataset. GPP time series were processed using statistical methods of time series decomposition. The results show that, in the alluvial domains, we find grasslands (mostly), alluvial forests with the highest levels of GPP, and the largest legally protected areas. Spatial distribution of pasturelands across the entire basin is broad while croplands are concentrated mainly in geologically old and high plateaus. The time series analysis revealed the presence of intra- and inter-annual vegetation patterns and a continuous increase of GPP over time. The results contribute to the understanding of the linkages between land use changes and global carbon cycles by considering land use as a response of how the landscape is organized. The results may provide subsidies for public policies for the carbon budget equilibrium, conservation of biodiversity, and rational use of natural resources.
Article
In recent years, the Cerrado deforestation has increased considerably, reaching rates higher than in the Amazonian realm. Although the effects of deforestation are well known, the understanding of its drives at regional levels is incipient. Most studies consider that a driver influences deforestation likewise in all regions. However, deforestation has a strong spatial structure that can lead drivers to vary their influence on deforestation in different regions. Here, we evaluated the spatial variability in the relationship between the recent Cerrado deforestation and socioeconomic, environmental, and structural drivers at a regional scale. We used a geographically weighted regression (GWR) to assess the spatial variability of predictor variables. We identified regions that respond similarly to the drivers by grouping municipalities, considering their GWR coefficients through hierarchical clustering. The analyses that consider the spatial variability of predictors are more appropriated to assess the causes of recent deforestation. Remnant natural vegetation influenced the recent deforestation in all defined regions. Greater access to rural credit concession was the main driving force of deforestation in the northeast region defined here. Distance to roads increased deforestation in the northeast and north regions, while it inhibited deforestation in the central-east and southeast regions. Rainfall inhibited deforestation in the northeast, north, and southwest regions. Steep slope prevented deforestation mainly in the northeast, north, and southwest regions. Our results highlight that, to effectively reduce Cerrado deforestation, public policies should integrate strategies focusing not only at national and biome levels but also at the regional spatial level.