Acessibilidade / Reportar erro

Climate ethics, climate (un)justice and ethical-political disputes in the Brazilian Payments for Environmental Services

Abstract

From the perspective of climate ethics, this article proposes to analyse the Payments for Environmental Services (PES) at the local (case study in São Paulo) and national (National Plan for Payments for Environmental Services) dimensions. The practices observed in these Brazilian political arenas were assessed via content analysis; From the guiding principles of political action, we analyse the dynamics of public policymaking actors in the light of categories such as planned naturalness, decision-making plurality, generational benefit, energy location and access to knowledge and material (PLANB Index). The final considerations refer to the urgency of public climate policies aligned with a normative ethical horizon, which must consider local perspectives as the starting point that helps the fulfilment of multilateral global agreements.

Keywords:
Climate ethics; climate justice; ethical-political disputes; payments for environmental services; brazilian national PES policy

Resumo

Este artigo analisa, sob a ótica da ética climática, as políticas de Pagamento por Serviços Ambientais nas dimensões local (PSA em São Paulo) e nacional (Plano Nacional de PSA) e o nexo indissociável entre a ética e a dimensão política brasileira. Essa conexão remete a uma reflexão teórica entre as políticas de PSA e o confronto de princípios éticos, por vezes antagônicos. As práticas observadas nas arenas políticas brasileiras foram avaliadas via análise de conteúdo à luz das seguintes categorias: Pluralidade decisória, Localidade energética, Acesso ao conhecimento e ao recurso material, Naturalização planejada e Benefício geracional (PLANB Index). As análises dos resultados transferem à urgência de políticas climáticas alinhadas a um horizonte ético normativo que reduza as iniquidades sociais e climáticas simultaneamente, as quais devem considerar, em termos de escala, as perspectivas locais e o tempo de implementação em sintonia com os acordos globais multilaterais.

Palavras-chave:
Ética climática; justiça climática; disputas éticas-políticas; pagamentos por serviços ambientais; política nacional de PSA

Resumen

Este artículo propone analizar los principios éticos en la perspectiva de la justicia climática de la política socioambiental por el Pago por Servicios Ambientales en multiescalas. Nacionalmente, con el Plan Nacional de Pagos por Servicios Ambientales, y localmente, con PSA locales. La metodología utilizada fue la de análisis de contenido sobre las prácticas observadas en estas arenas políticas. En la perspectiva de la ética climática y de los principios orientadores del quehacer político, analizamos las dinámicas de los formuladores de políticas públicas, a la luz de categorías naturalidad planificada, pluralidad decisoria, beneficio generacional, localidad energética y accesos (PLANB Index). Las consideraciones finales remiten a la urgencia de la inclusión de la clave analítica de la ética climática, tanto para ampliar el campo teórico de la justicia socioambiental en la perspectiva latinoamericana con la proposición de nuevas categorías analíticas, como empíricamente, para analizar y formular políticas más eficaces a crisis climática.

Palabras-clave:
Ética climática; justicia climática; disputas ético-políticas; pago de servicios ambientales brasileños; plan nacional de pagos por servicios ambientales

1. Introduction

The vertiginous increase in the concentration of greenhouse gases (GHG) in the atmosphere, such as carbon dioxide (CO2), results in greater retention of heat and, consequently, changes in global temperatures and atmospheric circulation patterns. The effects resulting from those changes, such as temperature extremes and changes in periods of drought and precipitation, impact socioecological systems in various ways and intensities (MILANEZ; FONSECA, 2012MILANEZ, B., FONSECA, I.F. Climate justice: framing a new discourse in Brazil. Local Environment, v. 17, n. 10, p. 1063-1073, Nov 2012. Disponível em: http://www.tandfonline.com/doi/abs/10.1080/13549839.2012.714757. Acesso em 02 fev. 2022.
http://www.tandfonline.com/doi/abs/10.10...
).

Despite the strength of this theme and the urgency to seek “solutions motivated by ethical principles [...] and moral arguments” appropriate to climate effects, studies with an approach to environmental ethics and its relationship with politics are still developing (TREMMEL; ROBINSON, 2014TREMMEL, J. C.; ROBINSON, K. Climate ethics: Environmental justice and climate change. Bloomsbury Publishing, 2014.). This article discusses the connection between climate ethics and normative effects in the Brazilian political arena in two dimensions, the Brazilian National Policy for Payments for Environmental Services (PNPSA in Portuguese) - and a case study in São Paulo. That relationship is demonstrated from the theoretical-methodological and normative framework of climate ethics through the articulation between the reflective plans in the perspective of ethical principles and their normative effects from the political perspective of the moral content revealed by the categories used in this work.

In communities and regions with vulnerabilities, such as low-income populations, small farmers, and discriminated racial segments, the implications of climate change add to aspects such as food insecurity and limited access to health, which make them more intense (IPCC, 2018). In this context, the term climate justice is mobilised because it refers to differences in levels of exposure to such impacts and calls for policies and initiatives, guided by the ethics of human rights, that reduce the vulnerability of these groups (MILANEZ; FONSECA, 2012MILANEZ, B., FONSECA, I.F. Climate justice: framing a new discourse in Brazil. Local Environment, v. 17, n. 10, p. 1063-1073, Nov 2012. Disponível em: http://www.tandfonline.com/doi/abs/10.1080/13549839.2012.714757. Acesso em 02 fev. 2022.
http://www.tandfonline.com/doi/abs/10.10...
).

In ethics, different reflective theoretical approaches imply the normalisation of these policies differently (HEATH, 2021HEATH, Joseph. Philosophical Foundations of Climate Change Policy. Oxford: Oxford University Press, 2021). The link between the reflective and normative plans is inherent. The principles of climate ethics, such as planned naturalisation and intergenerational benefit, are inseparable from the implications, both in the formulation and implementation of these policies, and can lead to a reduction or expansion of inequalities and, consequently, the realisation of climate (in)justice (FLORIT, 2019FLORIT, L. F. Dos conflitos ambientais à ética socioambiental: um olhar a partir dos povos e comunidades tradicionais. Desenvolvimento e Meio Ambiente, v. 52, 2019.). If the effectiveness of climate policies fundamentally permeates ethical issues (CANEY; HEPBURN, 2011CANEY, S.; HEPBURN, C. Carbon Trading: Unethical, Unjust and Ineffective? Centre for Climate Change Economics and Policy Working Paper, n. 59, 2011. Disponível em https://www.cccep.ac.uk/publication/carbon-trading-unethical-unjust-and-ineffective-working-paper-49/ Acesso em 11 abr. 2021.
https://www.cccep.ac.uk/publication/carb...
), then how to overcome the ‘old climate paradigm,’ based on the development of GHG emissions that affect the climate and exacerbate inequalities, to achieve the goals of the Paris Agreement and reduce inequalities at local-regional level?

The Paris Agreement, signed in 2015 by the member countries of the Climate Convention, includes principles and rules with the proposition of environmental effectiveness and social equity, which are also guided by measures of an economic nature, associated or not with regulatory instruments and public policies, for the conservation, recovery, or compensation of environmental services (UNFCCC, 2015). Furthermore, the Agreement establishes that countries must self-determine their national contributions (NDC - Nationally Determined Contributions) (Article 4) via mitigation measures to reduce GHG emissions, as well as adaptation measures (Article 6) (UNFCCC, 2015). One of the support mechanisms for complying with the Brazilian NDCs, which appears in the updated version of the country’s first declaration1 1 - UNFCCC: https://www4.unfccc.int/sites/NDCStaging/Pages/Party.aspx?party=BRA is the Payment for Environmental Services (PSA). However, this alone does not guarantee the necessary change to mitigate the effects of the climate.

PES programs create mechanisms to assign values to ecosystems, especially monetary values (however, RINCÓN et al. 2019RINCÓN, A.R. et al. Applying integrated valuation of ecosystem services in Latin America: Insights from 21 case studies. Ecosystem Services, v.36, 100901, 2019. discuss the importance of including other values, such as relational values, in the monetary calculation) due to the role they play, such as climate regulation via carbon sequestration and incorporate them into decision-making (PASCUAL et al., 2014PASCUAL, U. et al. Social equity matters in payments for ecosystem services. Bioscience, v. 64, n. 11, p. 1027-1036, 2014. Disponível em https://doi.org/10.1093/biosci/biu146 Acesso em 10 mar. 2021.
https://doi.org/10.1093/biosci/biu146 ...
). Therefore, PES schemes become an instrumented means with the potential to reduce inequalities and expand governance and legal security in the socio-environmental success of achieving global climate goals (PASCUAL et al., 2014).

In this context, cosmovisions whose ethical principles are based on respect for oneself, others, and non-human Nature, such as Teko Porã (Guarani) or Buen Vivir (in Andean countries), play a central role in the paths towards sustainability (SCARANO et al., 2021SCARANO, F.R., PADGURSCHI, M.C.P., SANTOS, L.M.F., AGUIAR, A.C.F., CARNEIRO, B.L.R., PIRES, A.P.F. Para além dos Objetivos do Desenvolvimento Sustentável: desafios para o Brasil. Bio Diverso, v. 1, n. 1, 2021. Disponível em: https://www.seer.ufrgs.br/index.php/biodiverso/article/view/120366
https://www.seer.ufrgs.br/index.php/biod...
). For example, the combined use of annual plantations with native tree species, a common practice among traditional peoples (SCARANO et al., 2021), shades the plantation, reducing the impact of local temperature and improving soil quality, measures of adaptation to the climate while contributing to mitigation via carbon storage (VIGNOLA et al., 2015VIGNOLA, R. et al. 2015. Ecosystem-based adaptation for smallholder farmers: Definitions, opportunities and constraints. Agriculture, Ecosystems and Environment, n. 211, p. 126-132. DOI: 10.1016/j.agee.2015.05.013
https://doi.org/10.1016/j.agee.2015.05.0...
). Thus, it is essential to propose changes to existing structures and new mechanisms to reduce socio-environmental inequalities (FLEURY; MIGUEL; TADDEI, 2019FLEURY, L. C.; MIGUEL, J. C. H.; TADDEI, R. Mudanças climáticas, ciência e sociedade. Sociologias, v. 21, n. 51, p. 18-42, 2019. Disponível em http://dx.doi.org/10.1590/15174522-0215101 Acesso em 02 abr. 2021.
http://dx.doi.org/10.1590/15174522-02151...
) based on anthropocentric/ecocentric values (HEATH, 2021HEATH, Joseph. Philosophical Foundations of Climate Change Policy. Oxford: Oxford University Press, 2021) that result in more fair and equitable structures.

1.1 In brief: PES as a measure of local protection against climate effects

Environmental, or ecosystem, services are Nature’s contributions to human well-being (MEA 2005), which might result in monetary benefits, such as the pollination essential for agriculture productivity, or in aesthetic and cultural value benefits. In this sense, the PES is the mechanism of subsidies (monetary or non-monetary ways) by which the environmental conservation entities receive (provider-recipient) from those who use them (users-payers) through a voluntary transaction (WUNDER, 2005WUNDER, S. Payments for environmental services: Some nuts and bolts. Center for International Forestry Research (CIFOR), v. 9, 2005. Disponível em https://vtechworks.lib.vt.edu/bitstream/handle/10919/66932/2437_009_Infobrief.pdf Acesso em 01 mai. 2022.
https://vtechworks.lib.vt.edu/bitstream/...
; PAGIOLA; PLATAIS, 2007PAGIOLA, S.; PLATAIS, G. Payments for environmental services: from theory to practice. Washington: World Bank, 2007.; CANOVA et al., 2019CANOVA, M. A. et al. Different ecosystem services, same (dis)satisfaction with compensation: A critical comparison between farmers’ perception in Scotland and Brazil. Ecosystem Services, v. 35, p. 164-172, fev. 2019.). In an empirical and no normalised way, PES schemes began in Brazil in 2006, in the municipality of Extrema/MG, and since then, have been implemented in different regions of Brazil.

After ten years of this framework, Brazil ratified the Paris Agreement Convention on Climate Change that predicted, explicitly according to the update of the document in 2020², the PES schemes as the measures to comply with the self-determinations (NDC) and to contribute to the Paris Agreement. In addition, two other vital goals of the Brazilian NDC, focusing on the reduction of 37% of GHG emissions by 2025 and the possibility of 43% by 2030, consist in restoring 12 million hectares of native vegetation and strengthening the compliance of the Brazilian Native Vegetation Protection Law, or New Brazilian Forest Code (Law n.12.651/2012).

That law disposes of the PES measures as a local mechanism for deforestation reduction and its consequent environmental benefits. Conversely, it demonstrates legal approval problems, including the amnesty for illegal deforestation until 2008 (SOARES-FILHO et al., 2014SOARES-FILHO, B. et al. Cracking Brazil’s Forest Code. Science, v. 344, n. 6182, p. 363-364, 2014.). Additionally, the law permits the possibility of implementing PES as an instrument. However, it does not indicate the institutional and technical arrangements and funding sources for its implementation, leading to failure concerning reaching its potential of social inequalities alleviation and combating deforestation (CANOVA et al., 2019CANOVA, M. A. et al. Different ecosystem services, same (dis)satisfaction with compensation: A critical comparison between farmers’ perception in Scotland and Brazil. Ecosystem Services, v. 35, p. 164-172, fev. 2019.).

For example, the PES promotes no-fire farming practices in Acre. Nevertheless, the action tends to focus on old settlements with landscapes dominated by pastures and farmers with greater economic stability and market access (ELOY et al., 2012ELOY, L. et al. Payments for ecosystem services in Amazonia. The challenge of land use heterogeneity in agricultural frontiers near Cruzeiro do Sul (Acre, Brazil). Journal of Environmental Planning and Management, v. 55, n. 6, p. 685-703, 2012. Disponível em doi/10.1080/09640568.2011.621021 Acesso em 30 mar. 2021
https://doi.org/10.1080/09640568.2011.62...
). Equity also involves non-material values, cultural identities, and different knowledge systems, such as from indigenous peoples (RINCÓN et al., 2019RINCÓN, A.R. et al. Applying integrated valuation of ecosystem services in Latin America: Insights from 21 case studies. Ecosystem Services, v.36, 100901, 2019.). Incentives that neglect all these complexities end up ignoring the vast conservation experience of these populations, besides exacerbating the inequalities (PASCUAL et al., 2014PASCUAL, U. et al. Social equity matters in payments for ecosystem services. Bioscience, v. 64, n. 11, p. 1027-1036, 2014. Disponível em https://doi.org/10.1093/biosci/biu146 Acesso em 10 mar. 2021.
https://doi.org/10.1093/biosci/biu146 ...
). Fifteen years after the first Brazilian initiative, the National Political for Ecosystem Services was instituted at the beginning of 2021 (PNPSA: lei 14.119; BRASIL, 2021).

The PES and its relationship with the public authority sphere are roughly addressed from the perspectives of natural sciences with geo-scientific implications (PENKAITIS; IMBERNON; DE VASCONCELO, 2020PENKAITIS, G.; IMBERNON, R. A. L.; DE VASCONCELOS, C. M. S. Pagamento por Serviços Ambientais (PSA): o papel do conhecimento geocientífico no protagonismo social. Terræ Didatica, 16, e020025-e020025, 2020.) and do not by a socio-political ambit that the present study seeks to demonstrate.

2. Methods

2.1 Theoretical framework

This article mobilises climate ethics as a theoretical-methodological framework, and the empirical object is Payment for Ecosystem Services (PES) at two levels (local and national). The content analysis method (BARDIN, 2009) is used, and the categories of socio-climate ethics (SALMI, 2021aSALMI, F. A emergente ética climática como instrumento de reordenamento sociopolítico. In: Problemas socioambientais emergentes: contribuições teóricas e práticas. TEIXEIRA, Rylanneive (org.). São Paulo: Gradus, 2021a. E-book. Disponível em https://www.graduseditora.com/problemassocioambientais Acesso em 23 jun. 2021.
https://www.graduseditora.com/problemass...
, 2021b) guide the content analyses. Finally, a theoretical model was developed (Figure 1).

The different dimensions (Figure 1, in grey) are layers of the theoretical-methodological framework. Worldviews are intertwined with principles, resulting in practices guided (by principles) at different spatial scales (see item 2.4). Theoretical elements can be assigned to each dimension, sometimes interconnecting them (Figure 1, in blue, red, and violet). The empirical objects are distributed in their respective dimensions (Figure 1, in yellow). Based on this model, the present study evaluates the empirical objects: 1) PES in the micro-region of Rio Claro, State of São Paulo, and 2) Brazilian National Policy for Payment for Ecosystem Services (PNPSA). The analytical objects are the narratives produced by local social agents (e.g., small and medium-sized farmers) and by PES policymakers at both levels (national and local).

The methodological approach for data collection involved individual and collective interviews through participatory workshops at the local level (CANOVA, 2016CANOVA, M. A. Construção de mecanismos de pagamento por serviços ambientais no cinturão de cana-de-açúcar do interior paulista através de métodos participativos. [s.l.] Universidade Estadual Paulista Júlio de Mesquita Filho (UNESP), 2016.). For the national level, we carried out documentary research on the official websites of the National Congress and the websites of public policymakers2 2 - The following organizations were also considered: Instituto Manejo e Certificação Florestal e Agrícola (IMAFLORA), Instituto Socioambiental (ISA), Article 19 and Coalizão Brasil Clima, Florestas e Agricultura (COALIZÃO). in the third sector until the official publication of the PNPSA. These data were analysed using five categories of socio-climate ethics - PLANB Index: decision-making Plurality, energy in the Locality, Access to knowledge and material resources, planned Naturalization, and (intra/inter) generational Benefit (SALMI, 2021bSALMI, F. Ética socioclimática e categorias analíticas: Potencial teórico-normativo para formuladores de políticas. Geotemas, v. 11, p. e02105-e02105, 2021b. Disponível em https://periodicos.apps.uern.br/index.php/GEOTemas/article/view/2951/2675 Acesso em 04 mai. 2023.
https://periodicos.apps.uern.br/index.ph...
). In the present study, the object of analysis was not the scale - although important - but the intertwinements and implications between the ethical and the political dimensions.

Figure 1
The theoretical model of political ontoethics in various scales and dimensions

2.2 Local study area

In order to investigate the establishment of Payment for Ecosystem Services (PES) on a local policy scale, the case study was conducted in the micro-region of Rio Claro in the region of Campinas/State of São Paulo, embracing either the proper Rio Claro Town and its Ferraz and Ajapí districts, or some neighbouring municipalities as Corumbataí, Santa Gertrudes, Ipeúna, Limeira, Cordeirópolis and Piracicaba. Brazil has unprecedented growth in sugarcane agribusiness production (CEPAL, 2005; LAPOLA et al., 2014LAPOLA, D. M. et al. Pervasive transition of the Brazilian land-use system. Nature Climate Change, v. 4, n. 1, p. 27-35, 2014. Disponível em https://doi.org/10.1038/nclimate2056 Acesso em 20 mar. 2021
https://doi.org/10.1038/nclimate2056 ...
). Over 50% of the cultivated area (in almost 5 million hectares at harvest 2020/2021) and 45% of ethanol distillation of the country’s sugarcane are located inSão Paulo State, the so-called “sugarcane belt” (UNICA, 2022).

The study area is situated in the transition zone between the Atlantic Forest and Cerrado biomes, where the process of land use and occupation for sugarcane agribusiness at the beginning of the XIX century (DEAN, 1996DEAN, W. A ferro e fogo: a história e a devastação da Mata Atlântica brasileira. 1. ed. São Paulo: Companhia das Letras, 1996.; GARCIA et al., 2006GARCIA, G. J. et al. Impact of land use on soil erosion and on the water balance and water quality in the Corumbataí watershed-SP. Holos Environment, n. 2, 2006.), but at the beginning of the XX century the region experienced a moderate production growth. However, in the 1970s, due to Brazilian federal incentives for ethanol fuel (Proálcool), the sugarcane expansion gained strength (GARCIA et al., 2006) and triggered a deficit of 50-70% of the forest remnants into private farms (BRASIL, 2012; SOARES-FILHO et al., 2014SOARES-FILHO, B. et al. Cracking Brazil’s Forest Code. Science, v. 344, n. 6182, p. 363-364, 2014.). As a result, the Rio Claro micro-region holds only 6% of natural vegetation cover (SIFESP, 2009), representing an extensive shifting of the regional landscape and consequently jeopardising the quality and provisioning of ES. Given that, studies must incorporate synergic alternatives of environmental protection, social support, and agriculture activities in the same way that PES schemes propose in theory.

2.3 Interviews and climate agents

The collected data from interviews were placed in two steps between 2014 and 2015. The first step was the conducting of individual semi-structured interviews (35 questions) employed with 39 local farmers (potential ecosystem services providers), of which three questions were used for this article: “Have you ever heard about Payment For Ecosystem Services? If yes, what are the region’s most significant obstacles to access to environmental compensation instruments? If not, to what do you attribute your unawareness of PSA schemes? The inquiries aimed to point out how much environmental public policy drafting involves the interest of multiple climate agents, one of the assumptions for socio-climate ethics. The complete questionnaire can be accessed in CANOVA (2016CANOVA, M. A. Construção de mecanismos de pagamento por serviços ambientais no cinturão de cana-de-açúcar do interior paulista através de métodos participativos. [s.l.] Universidade Estadual Paulista Júlio de Mesquita Filho (UNESP), 2016.).

The farmers’ sample was gathered through the farmers union tied to Rio Claro’s Agriculture Secretariat (Secretaria Municipal de Agricultura, Secretaria Municipal de Ação Social, Sindicato Patronal Rural, Cooperativa de Produtores) and the contributions of other farmers. They were equally divided between staple food producers, mainly vegetables (n=20) and sugarcane producers (n=19 + n=1, waiver) as the main activity, given that many have livestock production as a secondary activity. In the majority, the interviews were carried out at the agricultural facilities of interviewees, which enabled direct observation of farmers’ activities. This approach consists of a source of evidence, which can assist context comprehension and the phenomenon under study. Nonetheless, some farmers felt more comfortable being interviewed in Rio Claro’s Agriculture Secretariat or their households because many live in urban areas.

The participatory method (ROWE, FREWER, 2005ROWE, G.; FREWER, L. J. A Typology of Public Engagement Mechanisms. Science, Technology, & Human Values, v. 30, n. 2, p. 251-290, 18 abr. 2005.; WALLS; ROWE; FREWER, 2011WALLS, J.; ROWE, G.; FREWER, L. Stakeholder engagement in food risk management. Public Understanding of Science, v. 20, n. 2, p. 241-260, 2011.) was used for the second data collection step. The goal was to investigate how dialogue is established among multiple climate agents so that each participant could contribute with their perspective and thus achieve a common denominator for operationalizing the PES. A workshop was proposed with 30 climate agents composed of a heterogeneous group - public, private, and third sector agents - (decision-makers, policymakers, sugarcane, and food farmers, Non-Governmental Organization representatives, and researchers), whom, during the day, explained and discussed critical point view, as well as, some measures to employ the PES on the study area. All farmers interviewed (n=39) were invited to a workshop, but only 15 of them took part.

The workshop was divided into (i) a brief explanation regarding PES concepts and the relationship with Brazilian Legislation; (ii) a random division of the 30 climate agents into four subgroups, and for each was suggested a discussion and collective construction of dialogue and answers about ES, threats to ES, likely ES evaluation and obstacles to PES implantation. Finally, the focal group reorganised themselves for consensus dialogue surrounding the answers.

2.4 Nexus between socio-climate ethics theoretical-methodological framework and Brazilian Payment for Ecosystem Services (PES) policies

The thesis that “climate change is fundamentally an ethical issue” (GARDINER, 2017GARDINER, S. M. Climate ethics in a dark and dangerous time. Ethics, v. 127, n. 2, p. 430-465, 2017. Disponível em www.journals.uchicago.edu/doi/abs/10.1086/688746 Acesso em 30 mar. 2021.
www.journals.uchicago.edu/doi/abs/10.108...
, p.431) shows how climate as a political concept in dispute is complex. Currently, solutions to climate emergencies - for formulating climate policies - are guided by techno-economics logic and principles (OTTO et al., 2020OTTO, I. et al.. Social tipping dynamics for stabilizing Earth’s climate by 2050. Proceedings of the National Academy of Sciences, v. 117, n. 5, p. 2354-2365, 2020. DOI: 10.1073/pnas.1900577117 Acesso em: 24 jun. 2021.
https://doi.org/10.1073/pnas.1900577117...
). In Latin America, socio-environmental policies operate guided by neo-extractivist ethics3 3 - For a critical discussion about (neo)extractive liberal capitalism and its historical, geopolitical, social, and ecological implications in Latin America, see SVAMPA, 2019. and, therefore, anthropocentric since it does not recognize Nature as worthy of value in itself (ACOSTA; BRAND, 2018ACOSTA, A.; BRAND, U. Pós-extrativismo e decrescimento: saídas do labirinto capitalista. São Paulo: Elefante, 2018; TSING, 2019TSING, A. Viver nas ruínas: paisagens multiespécies no Antropoceno. Brasília: IEB Mil Folhas, 2019.; GUDYNAS, 2019GUDYNAS, E. Direitos da natureza: ética biocêntrica e políticas ambientais. Editora Elefante, 2019.; KOTHARI et al., 2019KOTHARI, A.; SALLEH, A.; ESCOBAR, A.; DEMARIA, F.; ACOSTA, A. Pluriverse. A Post-Development Dictionary. New Delhi: Tulika Books, 2019.). From this perspective, we argue that the discussion of public policies should be directly related to the discussion of cosmovisions and ethical principles4 4 - The Constitutions of Ecuador and Bolivia are examples of normative-political rearrangements with environmental policies formulated, also in the light of the ontoethical dimension that resulted in the consideration of Nature as a subject of rights (GUDYNAS, 2019). .

Ontologies and ‘cosmo-justices’ are crucial for societies to achieve ‘fair and justifiable agreements’ in overcoming socio-environmental conflicts by constructing fair policies (ALMEIDA, 2020ALMEIDA, J. (org.). Pesquisa em desenvolvimento, ambiente e conflitos. Curitiba: Appris, 2020.). The cosmovision is in a stratum where human and non-human beings perceive, feel, and produce themselves and the world subjectively around them (Figure 1, inner circle, dark grey). From this approach, ethical principles are unfolding (LEFF, 2015LEFF, E. Ecologia Política: uma perspectiva latino-americana. Desenvolvimento e Meio Ambiente, v. 35, 2015. Disponível em https://doi.org/10.5380/dma.v35i0.44381 Acesso em 11 mar. 2021.
https://doi.org/10.5380/dma.v35i0.44381 ...
; FLORIT, 2019FLORIT, L. F. Dos conflitos ambientais à ética socioambiental: um olhar a partir dos povos e comunidades tradicionais. Desenvolvimento e Meio Ambiente, v. 52, 2019.), like buen vivir of the Andean regions - principles embodied in the national policies of Ecuador and Bolivia (e.g., rights of Mother Earth) - KOTHARI et al., 2019KOTHARI, A.; SALLEH, A.; ESCOBAR, A.; DEMARIA, F.; ACOSTA, A. Pluriverse. A Post-Development Dictionary. New Delhi: Tulika Books, 2019. (Figure 1, outermost circles, intermediate gray, red, and violet from the ethical dimension). This political action in the world (empirical-political dimension), also called moralities or practices (morals), generates social interactions that can change structures5 5 - We mobilise the theoretical-methodological framework from Ricoeur (1992, p.172, emphasis in the original) that defines “ethical intention” as aiming at the “good life” with and for others in just institutions Ricoeur (1992, p.172, emphasis in the original version). In this way, we capture the agents’ “ethical intention.” and transform them into fairer institutions (RICOEUR, 1992RICOEUR, Paul. Oneself as Another. Chicago: University of Chicago Press, 1992., italics in original).

In Brazil, Florit (2019FLORIT, L. F. Dos conflitos ambientais à ética socioambiental: um olhar a partir dos povos e comunidades tradicionais. Desenvolvimento e Meio Ambiente, v. 52, 2019., p. 262) understands “socio-environmental ethics [...] as the level of reflection that shapes an interface between environmental ethics and social studies of environmental inequities”. In this context, climate ethics seeks to investigate the relationship between socio-environmental ethics and social studies of climate inequalities (e.g., the increased vulnerability in humans and non-humans due to extreme weather effects on vulnerable groups). Roughly speaking, climate ethics investigates the social effects - on humans and non-humans - of climate change, and this field of study is at the nexus between the reflective and normative levels (TREMMEL; ROBINSON, 2014TREMMEL, J. C.; ROBINSON, K. Climate ethics: Environmental justice and climate change. Bloomsbury Publishing, 2014.; GARDINER, 2017GARDINER, S. M. Climate ethics in a dark and dangerous time. Ethics, v. 127, n. 2, p. 430-465, 2017. Disponível em www.journals.uchicago.edu/doi/abs/10.1086/688746 Acesso em 30 mar. 2021.
www.journals.uchicago.edu/doi/abs/10.108...
; HEATH, 2021HEATH, Joseph. Philosophical Foundations of Climate Change Policy. Oxford: Oxford University Press, 2021).

At the reflective level, socio-climate ethics (SALMI, 2021aSALMI, F. A emergente ética climática como instrumento de reordenamento sociopolítico. In: Problemas socioambientais emergentes: contribuições teóricas e práticas. TEIXEIRA, Rylanneive (org.). São Paulo: Gradus, 2021a. E-book. Disponível em https://www.graduseditora.com/problemassocioambientais Acesso em 23 jun. 2021.
https://www.graduseditora.com/problemass...
; 2021b) broadens the field of socio-environmental ethics and provides an emphasis on climate change and social studies of socioecological equity and inequity; in the analytical level, it implies the study of social relations that result from the consideration, or not, of Nature and non-humans as subjects (INTERNACIONAL CONVIVIALISTA, 2020). Here, when we frame the right of Nature from the perspective of socio-climate ethics, we understand that overcoming the society-Nature dichotomy lies in a social shift from an anthropocentric cosmovision to an ecocentric one (Figure 1, inner circle, dark grey). Finally, on the normative level, it implies assuming that individuals are moral agents capable of acting guided by ethical principles, and thus these agents can produce normative rules (e.g., legal, infra-legal rules, or consistent community practices) in their social environment through the formulation and implementation a variety of social climate policies. In its different scales, such as the PSA, such moral practices can be observed in climate policies.

3. Results & Discussion

Evoking the concept of socio-environmental effectiveness of theorists who normatively analyse Payment for Ecosystem Services - PES (MICKWITZ, 2003MICKWITZ, P. A Framework for Evaluating Environmental Policy Instruments. Evaluation, v. 9, n. 4, p. 415-436, 2003. Disponível em: http://journals.sagepub.com/doi/10.1177/135638900300900404. Acesso em: 02 fev. 2022
http://journals.sagepub.com/doi/10.1177/...
; SATTLER et al., 2013SATTLER, C. et al. Multi-classification of payments for ecosystem services: How do classification characteristics relate to overall PES success? Ecosystem Services, v. 6, p. 31-45, dez. 2013., BERNARDO, 2016BERNARDO, K. T. Avaliação da efetividade de esquemas de pagamentos por serviços ambientais hídricos: proposta metodológica. [s.l.] Universidade de São Paulo, 2016.; GRIMA et al., 2016GRIMA, N. et al. Payment for Ecosystem Services (PES) in Latin America: Analysing the performance of 40 case studies. Ecosystem Services, v. 17, p. 24-32, 2016.), we introduce an analysis of PES policies, local and national, based on the categories of climate ethics (TREMMEL; ROBINSON, 2014TREMMEL, J. C.; ROBINSON, K. Climate ethics: Environmental justice and climate change. Bloomsbury Publishing, 2014.; GARDINER, 2017GARDINER, S. M. Climate ethics in a dark and dangerous time. Ethics, v. 127, n. 2, p. 430-465, 2017. Disponível em www.journals.uchicago.edu/doi/abs/10.1086/688746 Acesso em 30 mar. 2021.
www.journals.uchicago.edu/doi/abs/10.108...
; HEATH, 2021HEATH, Joseph. Philosophical Foundations of Climate Change Policy. Oxford: Oxford University Press, 2021; SALMI, 2021bSALMI, F. Ética socioclimática e categorias analíticas: Potencial teórico-normativo para formuladores de políticas. Geotemas, v. 11, p. e02105-e02105, 2021b. Disponível em https://periodicos.apps.uern.br/index.php/GEOTemas/article/view/2951/2675 Acesso em 04 mai. 2023.
https://periodicos.apps.uern.br/index.ph...
).

3.1 PES in the region of Rio Claro/SP and the localised climate (in)justice

From the universe of interviewed farmers, there was an equivalent percentage of those who had already heard about PES schemes (51%) and those who were unaware (49%), with most of the unaware being representatives of staple food farming. None of the farmers had participated in any action of PES mechanism construction. In addition, they mentioned that there are obstacles related to the role of state institutions (Table 1). These are agro energy/sugarcane farmers, which transfer production to the sugarcane mills, and consequently, a certification of the product is required to export it. Because of fulfilling those demands, the farmers likely have more access to information and, by extension, awareness of the PES.

Table 1
Engagement of interviewed farmers (n=39) in Payment for Ecosystem Services (PES) programs by food sector: food (n=20) and agro energy/sugarcane (n=19), as well as the mentioned obstacles in the interviews. The values are in percentage (%)

Through climate agent involvement, the data collection methodology permits a broader picture into ground-truth possibilities, which subside the policies realistically and inclusively, rather than including only specific scientific frameworks, ignoring the different possible approaches and their political implications for ecosystem management (SEPPELT, 2011SEPPELT, R. et al. A quantitative review of ecosystem service studies: Approaches, shortcomings and the road ahead. Journal of Applied Ecology, v. 48, n. 3, p. 630-636, 2011.). However, the process of public policy drafting for PES is frequently consummated without involving such primary conditions in the operationalization (CANOVA et al., 2019CANOVA, M. A. et al. Different ecosystem services, same (dis)satisfaction with compensation: A critical comparison between farmers’ perception in Scotland and Brazil. Ecosystem Services, v. 35, p. 164-172, fev. 2019.), resulting in a lack of information in relevant scales for decision-making, one of the obstacles that constrain a concept to be operationalized (TURNER; DAILY, 2008TURNER, R. K.; DAILY, G. C. The Ecosystem Services Framework and Natural Capital Conservation. Environmental and Resource Economics, v. 39, n. 1, p. 25-35, 6 jan. 2008.). The result shows that more than the existence of the PES instrument is needed for people to access it and leads us to the search for understanding the potential causes of non-participation of these local climate agents.

The climate agent’s narrative confronted with the normalisation operationalized by the public agents involved in the PES reveals, based on the categories of socio-climate ethics, some (in)justices. Access to awareness concerning the sociotechnical processes of mobilising funding resources for farmers is not a moral practice of local state policy6 6 - The premise that political practice is an oriented moral action (TREMMEL; ROBINSON, 2014, HEATH, 2021) refers in our context to a public policy guided by ethical principles — anthropocentric (e.g., liberal, extractivist) or ecocentric (e.g., preservationist, restorative). . On the one hand, public agents do not pragmatically release material resources, nor do they foster communication strategies and approximation between the different climate agents in terms of decision-making plurality in the PES arrangements. Thus, restoration can be accomplished (planned naturalisation). On the other hand, farmers and representatives’ agents cannot be involved in local PES arrangements because there is too much “bureaucracy”.

The farmers who reported PES unawareness attributed their reasons to points like those aware of the term (Table 1). The fact that there are similar reasons among the subsets demonstrates a policy of controlling sociotechnical knowledge (access to knowledge), shielding material resources (access to material resources), and a process of inhibiting plural participation in the various decision-making levels (decision-making plurality) of local PESs implementation processes.

In the present case study, the dialogues flourished from the perceptions of the multiple climate agents, who contributed to state decision makers supplying previous measures in PES projects, through the proposition of regulation of policies in the Municipality Director’s Plan and in the Municipality Environmental Law (CANOVA, 2016CANOVA, M. A. Construção de mecanismos de pagamento por serviços ambientais no cinturão de cana-de-açúcar do interior paulista através de métodos participativos. [s.l.] Universidade Estadual Paulista Júlio de Mesquita Filho (UNESP), 2016.). Os desdobramentos desse projeto foram implementados na Lei Complementar nº 128 de 07/12/2017, previsto no Art.125 como: “o município poderá utilizar-se do pagamento por serviços ambientais prestados por imóveis localizados na Macrozona de Preservação Ambiental e Uso Sustentável”.

The developments of this project were implemented in Complementary Law n. 128 of 07/12/2017, predicted in Article 125 as: “The municipality may make use of instruments of the Payment for Ecosystem Services provided by properties located in the “Macrozone of Environmental Preservation and Sustainable Use”.

The participation of farmers in argumentative processes and their engagement with public agents in the decision-making process (decision-making plurality) are fundamental aspects to give consistency and speed to the implementation of the PES at the local scale (energy in the locality). We emphasise that the moral implication with proposals for political regulation, for example, in the local PES schemes, must not be developed unilaterally, only with the participation of public agents.

3.2 The Brazilian National Policy for PES (PNPSA) as climate justice instrument at the macroscale

Aesthetic beauty, cultural importance, and evolutionary significance are non-monetary values ​​of Nature, and they have not been included in the current Brazilian Payment for Ecosystem Services (PES) mechanisms (McCAULEY, 2006; REDFORD; ADAMS, 2009REDFORD, K.H. & ADAMS, W.M. Payment for ecosystem services and the challenge of saving nature. Conservation biology, 23, 785-787, 2009.; RINCÓN et al., 2019RINCÓN, A.R. et al. Applying integrated valuation of ecosystem services in Latin America: Insights from 21 case studies. Ecosystem Services, v.36, 100901, 2019.). The challenge, therefore, is to project a monetary value to an intrinsic value of Nature in terms of PES (McCAULEY, 2006; REDFORD; ADAMS, 2009). On the other hand, PES programs have already demonstrated that they strengthen the relationship between land use and the conservation of natural resources, mainly in Latin America (GRIMA et al., 2016GRIMA, N. et al. Payment for Ecosystem Services (PES) in Latin America: Analysing the performance of 40 case studies. Ecosystem Services, v. 17, p. 24-32, 2016.; RINCÓN et al., 2019). From this perspective, PES can provide practical advances and materialise climate justice.

Since 2006, with the “Conservador das Águas” program in Extrema city, Minas Gerais state, other PES programs have been implemented in Brazil, as well as efforts to approve PES laws at different levels, from local to national (PAGIOLA, GLEHN, TAFFARELLO, 2013PAGIOLA, S.; VON-GLEHN, H. C.; TAFFARELLO, D. Brazil’s Experience with Payments for Environmental Services,World Bank Washington DC, EUA, 2013.). However, only in 2021 Brazil approves its Brazilian National Policy for Payment for Environmental Services - PNPSA (BRASIL, 2021). The PNPSA institutionalised and regulates PES programs at the local level, functioning as an umbrella for these initiatives.

The Brazilian PNPSA indicates, in Article 4, an integration with other sectoral and environmental policies, opening the possibility of convergence among them. Furthermore, this article establishes that the PES is an “instrument for promoting the social, environmental, economic and cultural development of rural producers in rural and urban areas, especially traditional communities, indigenous peoples and family farmers” (BRASIL, 2021). In this way, the Brazilian PNPSA can be an opportunity to break with the ‘old climate paradigm,’ overcome the society-Nature dichotomy and reduce GHG emissions and socio-environmental inequities.

However, the normative instruments include the PSA still in an incipient way. It is necessary to detail and operationalize financial, technical, and social mechanisms for its proper execution. Current programs are experimental, territorially restricted, and include few environmental services (e.g., maintenance of local water resources) (GUEDES, SEEHUSEN, 2011GUEDES, F. B.; SEEHUSEN, S. E. Pagamento por Serviços Ambientais na Mata Atlântica. Brasília: Ministério do Meio Ambiente, 2011.; PAGIOLA, GLEHN, TAFFARELLO, 2012PAGIOLA, S.; VON-GLEHN, H. C.; TAFFARELLO, D. Experiências de pagamentos por serviços ambientais no Brasil. São Paulo: Secretaria do Meio Ambiente / Coordenadoria de Biodiversidade e Recursos Naturais, 2012.). In addition, a few PES arrangements were monitored for socio-environmental effectiveness. These results are difficult to assess and need to be more documented.

For PES arrangements to be considered successful, certain conditions must be met (BERNARDO, 2016BERNARDO, K. T. Avaliação da efetividade de esquemas de pagamentos por serviços ambientais hídricos: proposta metodológica. [s.l.] Universidade de São Paulo, 2016.): 1) Prioritization of contracts that use ecological, social, economic, and regulatory criteria; 2) Participatory management (in addition to the consultation process) must include procedural fairness, i.e., the approach cannot be top-down; 3) A condition of equity and justice, based on equal rights, in addition to the aspirations of the agents directly involved. However, we argue that ontological disputes affect the political dimension (figure 1), in which conflicts can be observed.

Since 2019, access to information on environmental policies and democratic participation in decision-making spaces, until then, transparent and open, has been drastically restricted (decision-making plurality). Measures like the one that changed and/or extinguished fifty national councils public structures (access to knowledge) led to “blackouts in environmental databases, delegitimization and structural changes in public bodies responsible for producing data (access to material resources) about deforestation/regeneration Brazilian status’’ (IMAFLORA; ISA; ARTICLE19, 2021, p.2). According to the federal government, such actions would have the intention of providing “debureaucratization and reduction of the power of politically equipped entities [third sector environmental institutions] using ‘nice terms’ to impose their wills, ignoring the law, and purposely hindering the development of Brazil” (BOLSONARO, 2019BOLSONARO, J. Gigantesca economia, desburocratização e redução do poder [...]. S.l., 14 abr. 2019. Twitter: @jairbolsonaro. Disponível em: https://twitter.com/jairbolsonaro/status/ 1117441294048071682 Acesso em: 17 mar. 2021
https://twitter.com/jairbolsonaro/status...
). We question: “development” for whom? In this way, environmental entities - active until then in decision-making spaces in the public spheres --- were excised from these participatory processes (reduced decision-making plurality) and no longer had access to PES resources (lack of access to material resources). Such a forced “reduction of power” of legitimated and democratically organised civil society organisations (e.g., Imaflora, ISA) is a political action guided by a liberal authoritarian and neo-extractivist ethic.

In addition to the barriers imposed by the federal government, other institutions for civil society participation were extinguished, such as the National Commission for Agroecology and Organic Production (CNAPO) and the Guiding Committee of the Amazon Fund (COFA), or had their structures and resources reduced, such as the National Council for the Environment (CONAMA), Brazilian Forum on Climate Change (FBMC) and Management Committee of the National Fund for Climate Change. We can say that these democratic reductions are materialities, from an ethical and political perspective, of neoliberal neo-extractivist logic.

In January 2021, the publication of the Brazilian National Policy for PES followed anti-democratic practices (according to the lens of socio-climate ethics) due to vetoes in normative contents that could lead to the creation of a possible black box, guided by an “anti-republican and above all disrespectful strategy towards the legislative power” (LIMA, 2021LIMA, A. Vetos à Política de Pagamento por Serviços Ambientais criam possível caixa preta. Congresso em Foco, 15 jan. 2021. Disponível em https://congressoemfoco.uol.com.br/opiniao/colunas/vetos-a-politica-de-pagamento-por-servicos-ambientais-criam-possivel-caixa-preta/ Acesso em 20 jan. 2021.
https://congressoemfoco.uol.com.br/opini...
). Examples of this black box strategy include the ‘non-creation’ of a collegiate body for direct deliberation in decision-making processes by organised civil society institutions. Another example is the refusal to create “rules regarding PES contracts designed to provide legal certainty between the parties’’ (CAMARA DOS DEPUTADOS, 2021, p.1-4).

The multisectoral coalition ‘Coalizão Brasil Clima, Florestas e Agricultura’ also points out that the veto “removes not only the financial benefits and tax incentives (access to material resources and intragenerational and intergenerational benefit) but also the opportunity to promote credits with differentiated interest rates for activities for degraded areas’ recovery” (COALIZÃO, 2021, p.3). Meeting agents from the legislative branch (e.g., House of Representatives) with those from organised civil society (e.g., Coalizão Brasil Clima, Florestas e Agricultura, Instituto Socioambiental) reveals the ontoethical political disputes in the process of formulating this type of public policy. In March 2021, the Brazilian House of Representatives overrode some presidential vetoes, such as an article related to creating a collegiate body to make decisions about resources and one related to transparency contracts (CONGRESSO NACIONAL, 2021). It can be seen how planned structures at the national scale directly affect the local scale, for example, related to greater or lesser access to financial resources and better tax rates at/with local and national agents/structures.

The political dispute over certain moral practices (e.g., the normalisation or not of spaces for the inclusion of social participation) reveals how climate policymaking (such as PNPSA formulation) can provide the achievement or not of the Paris Agreement goals7 7 - By 2019, Brazil had reduced GHG by 17% (SEEG, 2021), considering 2005 levels. At this rate, the country will reduce by 30% instead of 37% by 2030, according to the current Brazilian NDC from the Paris Agreement (UNFCCC, 2022). . These political disputes are guided by ethical principles, as a rule, not explicitly, by the climate policymakers in the analysed Brazilian context.

Although these disputes have specificities (RIBEIRO, 2017RIBEIRO, W. C. Justiça espacial e justiça socioambiental: uma primeira aproximação. Estudos Avançados, v.31, n.89, 2017. Disponível em: http://dx.doi.org/10.1590/s0103-40142017.31890014 Acesso em 30 mar. 2021.
http://dx.doi.org/10.1590/s0103-40142017...
), ethical principles can be observed in multiple dimensions (e.g., sociological, ontological, epistemological) and scales (e.g., national, local) through the analytical lens of the PLANB Index. For example, without socio-environmental legal protection, it opens spaces for neoliberal enterprises to operate freely through unlimited exploitation and continuous deconfiguration of ecosystems. In this current, answering the question of how to formulate good climate policies at multiple scales is imperative.

From the perspective of socio-climate ethics and the guiding principles of socially oriented political action, by analysing the dynamics of policymaking agents in two interdependent dimensions (Figure 1), we observe how decision spaces are interconnected locally and nationally and the tensions between plural and inclusive environments and monocratic institutional structures as well its effects on the production of social equalities/inequalities and climate justice.

4. Final Remarks

To demonstrate how the ethical-political framework proposed here helps to reveal the guiding principles of political action that shape the structures of climate (in)justice, we assume as premises of the present study that (i) the principles for compensation of environmental services included in the Paris Agreement can help to overcome the old climate paradigm; (ii) the Payment for Ecosystem Services (PES) as a local climate mitigation mechanism proposed by the Brazilian NDC in 2020 can help to promote the achievement of goals and generate climate justice in practice provided that (iii) the PES is guided by the principles of socio-climate ethics as the normalizable categories of the PLANB Index.

In the local dimension, we show that failures to access knowledge and material resources and the absence of decision-making plurality in the PES decision-making process make it difficult to promote climate justice. That reveals the urgency of moral and political practices aimed at a new utopian horizon of effective ecological and economic transition. At the national level, we show that although the Brazilian National Policy for PES (PNPSA) has been instituted, it still needs mechanisms for better operationalization. In addition, in both dimensions, we observe a struggle between different worldviews: the anthropocentric and dominant, guided by a capitalist industrial urban ethic - among other principles, such as liberal, extractive, and authoritarian - and the ecocentric and emerging, which disputes structural remodelling. Thus, we argue that the ability to create new worlds to overcome the old climate paradigm becomes an ontoethical and methodological challenge in apprehending such moral practices at the political level.

There is still a long way to go in seeking inclusive socio-political climate architectures that reduce current social and ecological inequalities at various scales, from local to regional and national to global. Including scientific approaches with an interdisciplinary agenda like the one presented in this work may be one of those possible ways to overcome the dichotomous dogma (e.g., society-Nature, local-global, humans-non-humans). Based on our analyses, we argue that the conceptual framework and elements of socio-climate ethics can be the common thread that leads to the normalisation of climate policies based on ecocentric or even multicentric ethical principles. Otherwise, by neglecting the link between ethics and politics - and consequently the multiple conceptions of Nature - other cosmovisions and inclusive principles such as democratic values are abandoned. Neglecting just and justified agreements leads to dystopian horizons of authoritarian, hegemonic, and sometimes violent logic.

As a result, the reduction of the anthropic effects of climate change and the new climate utopian horizon planned by the Paris Agreement remains at imminent risk of not materialising. In this sense, climate inequalities tend to increase the social and ecological inequality gap. Therefore, the nexus between ethics and politics of the approach presented here is, in the Brazilian climate context - and on other scales - urgent and crucial to lead to new climate utopian horizons.

Acknowledgements

FS thanks to the Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq) for the master’s scholarship (UFRGS/CNPQ 133908/2020-8); MAC thanks to the Fundação de Amparo à Pesquisa do Estado de São Paulo for the doctoral scholarship (FAPESP 2019/02452-2); MCGP thanks to the Coordenação de Aperfeiçoamento de Pessoal de Nível Superior for the research fellowship (INPA/CAPES 88881.154644/2017-01). The authors thank the AmazonFace program (88887.373727/2019-00) for its research infrastructure and the Simpósio Nacional de Justiça Socioambiental (UFPR/2021) for the valuable comments. This research was conducted under the ethics commitments (CAAE: 33701814.9.0000.5465).

Referências

  • ACOSTA, A.; BRAND, U. Pós-extrativismo e decrescimento: saídas do labirinto capitalista. São Paulo: Elefante, 2018
  • ALMEIDA, J. (org.). Pesquisa em desenvolvimento, ambiente e conflitos. Curitiba: Appris, 2020.
  • BARDIN, L. Análise de Conteúdo. São Paulo: Edições 70, 2011.
  • BERNARDO, K. T. Avaliação da efetividade de esquemas de pagamentos por serviços ambientais hídricos: proposta metodológica. [s.l.] Universidade de São Paulo, 2016.
  • BOLSONARO, J. Gigantesca economia, desburocratização e redução do poder [...]. S.l., 14 abr. 2019. Twitter: @jairbolsonaro. Disponível em: https://twitter.com/jairbolsonaro/status/ 1117441294048071682 Acesso em: 17 mar. 2021
    » https://twitter.com/jairbolsonaro/status/ 1117441294048071682
  • BRASIL. Lei no 12.651, de 25 de maio de 2012. Dispõe sobre a proteção da vegetação nativa. Diário Oficial da União. Brasil, 2012. Disponível em: https://www.planalto.gov.br/ccivil_03/_ato2011-2014/2012/lei/L12651compilado.htm Acesso em 08 abr. 2021
    » https://www.planalto.gov.br/ccivil_03/_ato2011-2014/2012/lei/L12651compilado.htm
  • BRASIL. Lei n.º 14.119, de 13 de janeiro de 2021. Institui a Política Nacional de Pagamento por Serviços Ambientais, instituída em 13 de janeiro de 2021. Diário Oficial da União. Brasil, 2021. Disponível em https://www.in.gov.br/en/web/dou/-/lei-n-14.119-de-13-de-janeiro-de-2021-298899394 Acesso em 12 mar. 2021
    » https://www.in.gov.br/en/web/dou/-/lei-n-14.119-de-13-de-janeiro-de-2021-298899394
  • BROOKS, T. (Ed.). The Oxford Handbook of Global Justice. Oxford University Press, USA, 2020.
  • BROWN, D. A.; TAYLOR, Prue. Ethics and climate change: A study of national commitments. IUCN, 2015
  • CÂMARA DOS DEPUTADOS. Por uma política pública de meio ambiente participativa e transparente capaz de atrair investimentos para o desenvolvimento do país. Brasília, DF, 11 fev. 2021. Disponível em https://camaranet.camara.leg.br/edoc-ws/#/validaredoc/2021-XIKA-FWGB-GPIC-EQTV Acesso em 21 fev. 2021
    » https://camaranet.camara.leg.br/edoc-ws/#/validaredoc/2021-XIKA-FWGB-GPIC-EQTV
  • CANEY, S.; HEPBURN, C. Carbon Trading: Unethical, Unjust and Ineffective? Centre for Climate Change Economics and Policy Working Paper, n. 59, 2011. Disponível em https://www.cccep.ac.uk/publication/carbon-trading-unethical-unjust-and-ineffective-working-paper-49/ Acesso em 11 abr. 2021.
    » https://www.cccep.ac.uk/publication/carbon-trading-unethical-unjust-and-ineffective-working-paper-49
  • CANOVA, M. A. Construção de mecanismos de pagamento por serviços ambientais no cinturão de cana-de-açúcar do interior paulista através de métodos participativos. [s.l.] Universidade Estadual Paulista Júlio de Mesquita Filho (UNESP), 2016.
  • CANOVA, M. A. et al. Different ecosystem services, same (dis)satisfaction with compensation: A critical comparison between farmers’ perception in Scotland and Brazil. Ecosystem Services, v. 35, p. 164-172, fev. 2019.
  • CEPAL. COMISÍON ECONÓMICA PARA AMÉRICA LATINA Y EL CARIBE. El nuevo patrón de desarrollo de la agricultura en América Latina y el Caribe, 2005. Disponível em: https://www.cepal.org/sites/default/files/publication/files/31927/S2005039_es.pdf Acesso em 08 abr. 2021.
    » https://www.cepal.org/sites/default/files/publication/files/31927/S2005039_es.pdf
  • COALIZÃO Brasil Clima, Florestas e Agricultura. Observatório da Restauração e Reflorestamento. Observatório da Restauração e Reflorestamento, 2021. Disponível em https://observatoriodarestauracao.org.br/app/home Acesso em 15 mar. 2021
    » https://observatoriodarestauracao.org.br/app/home
  • CONGRESSO NACIONAL. Veto n.º 5/2021. Política Nacional de Pagamento por Serviços Ambientais. Disponível em https://www.congressonacional.leg.br/materias/vetos/-/veto/detalhe/13965 Acesso em 08 abr. 2021.
    » https://www.congressonacional.leg.br/materias/vetos/-/veto/detalhe/13965
  • CRESWELL, J. W. Investigação qualitativa e projeto de pesquisa: escolhendo entre cinco abordagens. 3. ed. Porto Alegre: Penso, pp. 341, 2014
  • DEAN, W. A ferro e fogo: a história e a devastação da Mata Atlântica brasileira. 1. ed. São Paulo: Companhia das Letras, 1996.
  • DIFFENBAUGH, N. S.; BURKE, M. Global warming has increased global economic inequality. Proceedings of the National Academy of Sciences, v. 116, n. 20, p. 9808-9813, 2019. https://www.pnas.org/content/116/20/9808 Acesso em 22 mar. 2021.
    » https://www.pnas.org/content/116/20/9808
  • ELOY, L. et al. Payments for ecosystem services in Amazonia. The challenge of land use heterogeneity in agricultural frontiers near Cruzeiro do Sul (Acre, Brazil). Journal of Environmental Planning and Management, v. 55, n. 6, p. 685-703, 2012. Disponível em doi/10.1080/09640568.2011.621021 Acesso em 30 mar. 2021
    » https://doi.org/10.1080/09640568.2011.621021
  • FLEURY, L. C.; MIGUEL, J. C. H.; TADDEI, R. Mudanças climáticas, ciência e sociedade. Sociologias, v. 21, n. 51, p. 18-42, 2019. Disponível em http://dx.doi.org/10.1590/15174522-0215101 Acesso em 02 abr. 2021.
    » http://dx.doi.org/10.1590/15174522-0215101
  • FLORIT, L. F. Dos conflitos ambientais à ética socioambiental: um olhar a partir dos povos e comunidades tradicionais. Desenvolvimento e Meio Ambiente, v. 52, 2019.
  • GARCIA, G. J. et al. Impact of land use on soil erosion and on the water balance and water quality in the Corumbataí watershed-SP. Holos Environment, n. 2, 2006.
  • GARDINER, S. M. Climate ethics in a dark and dangerous time. Ethics, v. 127, n. 2, p. 430-465, 2017. Disponível em www.journals.uchicago.edu/doi/abs/10.1086/688746 Acesso em 30 mar. 2021.
    » www.journals.uchicago.edu/doi/abs/10.1086/688746
  • GARNETT, S. T. et al. A spatial overview of the global importance of Indigenous lands for conservation. Nature Sustainability, 1: 369-374, 2018.
  • GUEDES, F. B.; SEEHUSEN, S. E. Pagamento por Serviços Ambientais na Mata Atlântica. Brasília: Ministério do Meio Ambiente, 2011.
  • GRIMA, N. et al. Payment for Ecosystem Services (PES) in Latin America: Analysing the performance of 40 case studies. Ecosystem Services, v. 17, p. 24-32, 2016.
  • GORENFLO, L. J. et al. Co-occurrence of linguistic and biological diversity in biodiversity hotspots and high biodiversity wilderness areas. Proceedings of the National Academy of Sciences, v. 109, n. 21, p. 8032-8037, 2012. Disponível em www.pnas.org/cgi/doi/10.1073/pnas.1117511109 Acesso em 30 mar. 2021.
    » www.pnas.org/cgi/doi/10.1073/pnas.1117511109
  • GUDYNAS, E. Direitos da natureza: ética biocêntrica e políticas ambientais. Editora Elefante, 2019.
  • HEATH, Joseph. Philosophical Foundations of Climate Change Policy. Oxford: Oxford University Press, 2021
  • IMAFLORA; ISA; ARTICLE19. Mapeamento dos retrocessos de transparência e participação social na política ambiental brasileira - 2019 e 2020. Disponível em https://www.imaflora.org/public/media/biblioteca/mapeamento_dos_retrocessos_de_transparencia_e_participacao_social_na_politica_ambiental_.pdf Acesso em 01 mar. 2021
    » https://www.imaflora.org/public/media/biblioteca/mapeamento_dos_retrocessos_de_transparencia_e_participacao_social_na_politica_ambiental_.pdf
  • INTERNACIONAL CONVIVIALISTA. Segundo Manifesto Convivialista: por um mundo pós-neoliberal. Rio de Janeiro: Ateliê das Humanidades, 2020.
  • IPCC. Global Warming of 1.5°C: Special Report on the impacts of global warming of 1.5°C above pre-industrial levels and related global greenhouse gas emission pathways, in the context of strengthening the global response to the threat of climate change, sustainable development, and efforts to eradicate poverty [Masson-Delmotte et al. (eds.)]. 2018. Disponível em http://www.ipcc.ch/sr15 Acesso em 02 mar 2022
    » http://www.ipcc.ch/sr15
  • KOTHARI, A.; SALLEH, A.; ESCOBAR, A.; DEMARIA, F.; ACOSTA, A. Pluriverse. A Post-Development Dictionary. New Delhi: Tulika Books, 2019.
  • LAPOLA, D. M. et al. Pervasive transition of the Brazilian land-use system. Nature Climate Change, v. 4, n. 1, p. 27-35, 2014. Disponível em https://doi.org/10.1038/nclimate2056 Acesso em 20 mar. 2021
    » https://doi.org/10.1038/nclimate2056
  • LECLÈRE, D. et al. Bending the curve of terrestrial biodiversity needs an integrated strategy. Nature, v. 585, n. 7826, p. 551-556, 2020. Disponível em https://doi.org/10.1038/s41586-020-2705-y Acesso em 02 abr. 2021.
    » https://doi.org/10.1038/s41586-020-2705-y
  • LEFF, E. Ecologia Política: uma perspectiva latino-americana. Desenvolvimento e Meio Ambiente, v. 35, 2015. Disponível em https://doi.org/10.5380/dma.v35i0.44381 Acesso em 11 mar. 2021.
    » https://doi.org/10.5380/dma.v35i0.44381
  • LIMA, A. Vetos à Política de Pagamento por Serviços Ambientais criam possível caixa preta. Congresso em Foco, 15 jan. 2021. Disponível em https://congressoemfoco.uol.com.br/opiniao/colunas/vetos-a-politica-de-pagamento-por-servicos-ambientais-criam-possivel-caixa-preta/ Acesso em 20 jan. 2021.
    » https://congressoemfoco.uol.com.br/opiniao/colunas/vetos-a-politica-de-pagamento-por-servicos-ambientais-criam-possivel-caixa-preta
  • MCCAULEY, D.J. Selling out on nature. Nature, n. 443, p. 27-28, 2006.
  • MILLENIUM ECOSYSTEM ASSESSMENT (MEA). Ecosystems and Human Well-being: Synthesis. Washington, DC Island Press, 2005.
  • MILANEZ, B., FONSECA, I.F. Climate justice: framing a new discourse in Brazil. Local Environment, v. 17, n. 10, p. 1063-1073, Nov 2012. Disponível em: http://www.tandfonline.com/doi/abs/10.1080/13549839.2012.714757 Acesso em 02 fev. 2022.
    » http://www.tandfonline.com/doi/abs/10.1080/13549839.2012.714757
  • MICKWITZ, P. A Framework for Evaluating Environmental Policy Instruments. Evaluation, v. 9, n. 4, p. 415-436, 2003. Disponível em: http://journals.sagepub.com/doi/10.1177/135638900300900404 Acesso em: 02 fev. 2022
    » http://journals.sagepub.com/doi/10.1177/135638900300900404
  • OTTO, I. et al.. Social tipping dynamics for stabilizing Earth’s climate by 2050. Proceedings of the National Academy of Sciences, v. 117, n. 5, p. 2354-2365, 2020. DOI: 10.1073/pnas.1900577117 Acesso em: 24 jun. 2021.
    » https://doi.org/10.1073/pnas.1900577117
  • PAGIOLA, S.; PLATAIS, G. Payments for environmental services: from theory to practice. Washington: World Bank, 2007.
  • PAGIOLA, S.; VON-GLEHN, H. C.; TAFFARELLO, D. Experiências de pagamentos por serviços ambientais no Brasil. São Paulo: Secretaria do Meio Ambiente / Coordenadoria de Biodiversidade e Recursos Naturais, 2012.
  • PAGIOLA, S.; VON-GLEHN, H. C.; TAFFARELLO, D. Brazil’s Experience with Payments for Environmental Services,World Bank Washington DC, EUA, 2013.
  • PASCUAL, U. et al. Social equity matters in payments for ecosystem services. Bioscience, v. 64, n. 11, p. 1027-1036, 2014. Disponível em https://doi.org/10.1093/biosci/biu146 Acesso em 10 mar. 2021.
    » https://doi.org/10.1093/biosci/biu146
  • PENKAITIS, G.; IMBERNON, R. A. L.; DE VASCONCELOS, C. M. S. Pagamento por Serviços Ambientais (PSA): o papel do conhecimento geocientífico no protagonismo social. Terræ Didatica, 16, e020025-e020025, 2020.
  • REDFORD, K.H. & ADAMS, W.M. Payment for ecosystem services and the challenge of saving nature. Conservation biology, 23, 785-787, 2009.
  • RIBEIRO, W. C. Justiça espacial e justiça socioambiental: uma primeira aproximação. Estudos Avançados, v.31, n.89, 2017. Disponível em: http://dx.doi.org/10.1590/s0103-40142017.31890014 Acesso em 30 mar. 2021.
    » http://dx.doi.org/10.1590/s0103-40142017.31890014
  • RINCÓN, A.R. et al. Applying integrated valuation of ecosystem services in Latin America: Insights from 21 case studies. Ecosystem Services, v.36, 100901, 2019.
  • RICOEUR, Paul. Oneself as Another. Chicago: University of Chicago Press, 1992.
  • RITCHIE, H.; ROSER, M. CO2 and other greenhouse gas emissions. Our world in data, 2020. Disponível em https://ourworldindata.org/co2-and-other-greenhouse-gas-emissions Acesso em 30 mar. 2021
    » https://ourworldindata.org/co2-and-other-greenhouse-gas-emissions
  • ROWE, G.; FREWER, L. J. A Typology of Public Engagement Mechanisms. Science, Technology, & Human Values, v. 30, n. 2, p. 251-290, 18 abr. 2005.
  • SALMI, F. A emergente ética climática como instrumento de reordenamento sociopolítico. In: Problemas socioambientais emergentes: contribuições teóricas e práticas. TEIXEIRA, Rylanneive (org.). São Paulo: Gradus, 2021a. E-book. Disponível em https://www.graduseditora.com/problemassocioambientais Acesso em 23 jun. 2021.
    » https://www.graduseditora.com/problemassocioambientais
  • SALMI, F. Ética socioclimática e categorias analíticas: Potencial teórico-normativo para formuladores de políticas. Geotemas, v. 11, p. e02105-e02105, 2021b. Disponível em https://periodicos.apps.uern.br/index.php/GEOTemas/article/view/2951/2675 Acesso em 04 mai. 2023.
    » https://periodicos.apps.uern.br/index.php/GEOTemas/article/view/2951/2675
  • SATTLER, C. et al. Multi-classification of payments for ecosystem services: How do classification characteristics relate to overall PES success? Ecosystem Services, v. 6, p. 31-45, dez. 2013.
  • SCARANO, F.R., PADGURSCHI, M.C.P., SANTOS, L.M.F., AGUIAR, A.C.F., CARNEIRO, B.L.R., PIRES, A.P.F. Para além dos Objetivos do Desenvolvimento Sustentável: desafios para o Brasil. Bio Diverso, v. 1, n. 1, 2021. Disponível em: https://www.seer.ufrgs.br/index.php/biodiverso/article/view/120366
    » https://www.seer.ufrgs.br/index.php/biodiverso/article/view/120366
  • SEEG. SISTEMA DE ESTIMATIVA DE EMISSÕES DE GASES DE EFEITO ESTUFA. SEEG. Disponível em http://plataforma.seeg.eco.br/total_emission# Acesso em 20 mar. 2021.
    » http://plataforma.seeg.eco.br/total_emission#
  • SEPPELT, R. et al. A quantitative review of ecosystem service studies: Approaches, shortcomings and the road ahead. Journal of Applied Ecology, v. 48, n. 3, p. 630-636, 2011.
  • SIFESP. SISTEMA DE INFORMAÇÕES FLORESTAIS DO ESTADO DE SÃO PAULO [2009]. Disponível em:< http://www.iflorestal.sp.gov.br>. Acesso em 02 fev. 2022
    » http://www.iflorestal.sp.gov.br
  • SOARES-FILHO, B. et al. Cracking Brazil’s Forest Code. Science, v. 344, n. 6182, p. 363-364, 2014.
  • STOCK, A. et al. A Justiça Socioecológica e suas dimensões: o Acolhida na Colônia no estado de Santa Catarina, Brasil. Guaju, v. 4, n. 2, p. 86-99, 2018. Disponível em https://revistas.ufpr.br/guaju/article/download/57445/37346 Acesso em 30 mar. 2021.
    » https://revistas.ufpr.br/guaju/article/download/57445/37346
  • SVAMPA, M. As fronteiras do neoextrativismo na América Latina: Conflitos socioambientais, giro ecoterritorial e novas dependências. São Paulo: Elefante, 2019.
  • TSING, A. Viver nas ruínas: paisagens multiespécies no Antropoceno. Brasília: IEB Mil Folhas, 2019.
  • TREMMEL, J. C.; ROBINSON, K. Climate ethics: Environmental justice and climate change. Bloomsbury Publishing, 2014.
  • TURNER, R. K.; DAILY, G. C. The Ecosystem Services Framework and Natural Capital Conservation. Environmental and Resource Economics, v. 39, n. 1, p. 25-35, 6 jan. 2008.
  • UNFCCC - UNITED NATIONS FRAMEWORK CONVENTION ON CLIMATE CHANGE. The Paris Agreement. 2015. Disponível em http://unfccc.int/paris_agreement/items/9485.php Acesso 17 jun. 2021.
    » http://unfccc.int/paris_agreement/items/9485.php
  • UNFCCC - UNITED NATIONS FRAMEWORK CONVENTION ON CLIMATE CHANGE. Nationally Determined Contributions Registry. 2022. Disponível em https://unfccc.int/sites/default/files/NDC/2022-06/Updated%20-%20First%20NDC%20-%20%20FINAL%20-%20PDF.pdf Acesso 28 ago. 2022
    » https://unfccc.int/sites/default/files/NDC/2022-06/Updated%20-%20First%20NDC%20-%20%20FINAL%20-%20PDF.pdf
  • UNICA. UNIÃO DA INDÚSTRIA DE CANA-DE-AÇÚCAR. Observatório da Cana. 2022. Disponível em: https://observatoriodacana.com.br Acesso em 28 ago. 2022.
    » https://observatoriodacana.com.br
  • VIGNOLA, R. et al. 2015. Ecosystem-based adaptation for smallholder farmers: Definitions, opportunities and constraints. Agriculture, Ecosystems and Environment, n. 211, p. 126-132. DOI: 10.1016/j.agee.2015.05.013
    » https://doi.org/10.1016/j.agee.2015.05.013
  • WALLS, J.; ROWE, G.; FREWER, L. Stakeholder engagement in food risk management. Public Understanding of Science, v. 20, n. 2, p. 241-260, 2011.
  • WELLS, G. B.; GUNTHER, M. G. De crisis, ecologías y transiciones: reflexiones sobre teoría social latinoamericana frente al cambio ambiental global. Revista Colombiana de Sociología, v. 42, n. 1, p. 19-40, 2019. Disponível em doi/10.15446/rcs.v42n1.73190 Acesso em 01 mar. 2021.
  • WUNDER, S. Payments for environmental services: Some nuts and bolts. Center for International Forestry Research (CIFOR), v. 9, 2005. Disponível em https://vtechworks.lib.vt.edu/bitstream/handle/10919/66932/2437_009_Infobrief.pdf Acesso em 01 mai. 2022.
    » https://vtechworks.lib.vt.edu/bitstream/handle/10919/66932/2437_009_Infobrief.pdf
  • 1
    - UNFCCC: https://www4.unfccc.int/sites/NDCStaging/Pages/Party.aspx?party=BRA
  • 2
    - The following organizations were also considered: Instituto Manejo e Certificação Florestal e Agrícola (IMAFLORA), Instituto Socioambiental (ISA), Article 19 and Coalizão Brasil Clima, Florestas e Agricultura (COALIZÃO).
  • 3
    - For a critical discussion about (neo)extractive liberal capitalism and its historical, geopolitical, social, and ecological implications in Latin America, see SVAMPA, 2019.
  • 4
    - The Constitutions of Ecuador and Bolivia are examples of normative-political rearrangements with environmental policies formulated, also in the light of the ontoethical dimension that resulted in the consideration of Nature as a subject of rights (GUDYNAS, 2019).
  • 5
    - We mobilise the theoretical-methodological framework from Ricoeur (1992, p.172, emphasis in the original) that defines “ethical intention” as aiming at the “good life” with and for others in just institutions Ricoeur (1992, p.172, emphasis in the original version). In this way, we capture the agents’ “ethical intention.”
  • 6
    - The premise that political practice is an oriented moral action (TREMMEL; ROBINSON, 2014, HEATH, 2021) refers in our context to a public policy guided by ethical principles — anthropocentric (e.g., liberal, extractivist) or ecocentric (e.g., preservationist, restorative).
  • 7
    - By 2019, Brazil had reduced GHG by 17% (SEEG, 2021), considering 2005 levels. At this rate, the country will reduce by 30% instead of 37% by 2030, according to the current Brazilian NDC from the Paris Agreement (UNFCCC, 2022).

Publication Dates

  • Publication in this collection
    17 July 2023
  • Date of issue
    2023

History

  • Received
    06 Sept 2021
  • Accepted
    25 Nov 2022
ANPPAS - Revista Ambiente e Sociedade Anppas / Revista Ambiente e Sociedade - São Paulo - SP - Brazil
E-mail: revistaambienteesociedade@gmail.com