The following discussion is divided into four domains of action, categorised as Climate Change, bioenergy and biofuels (4.1), Global Syndemic and food security (4.2); Family farming and public policy (4.3) and Specific biomes and deforestation (4.4). The discussion is based on the evidence from the scoping review and is enriched by specific linkages with some of the 169 SDG targets.
4.1. Climate Change, bioenergy and biofuels
Biofuel production and land use for agriculture are one of Brazil's most significant and contextual trade-offs when it comes to sustainable development, explicitly represented by the bioethanol clean energy production from sugarcane. Sugarcane production is a historic part of the nation's development, intertwined with Brazilian society's socio-economic configuration. The slavery-based cotton plantations represented in the United States can be paralleled with the Brazilian sugarcane plantations (Schwartz, 1985). In 1975, the Brazilian government implemented the Brazilian Alcohol Program (Proalcool) (target 13.2), aimed at reducing oil exports. In Brazil, ethanol is blended into gasoline as an octane enhancer (Goldemberg, Coelho & Guardabassi, 2008). Socio-environmental impacts related to sugarcane can be linked to pollution-related health issues (target 3.9) (Arbex et al., 2007), labour force exploitation (target 8.7) (Rocha, Marziale & Hong, 2010), soil degradation (target 12.4 and 2.4) (Vera, Wicke & Hilst, 2020), among others. When it comes to greenhouse gas emissions (target 13.1), some studies portray Brazilian sugarcane fields as CO2 sinks, absorbing more carbon than releasing it into the atmosphere (Cabral et al., 2020), while other authors suggest that changing the land-use, for instance, from coffee to sugarcane, can hinder the system sustainability (de Oliveira Bordonal et al., 2017).
When it comes to food security, the crossroads linking the topics form a nexus relating water-food-energy (Benites-Lazaro et al., 2018). The clash between food-security and the green biofuel production has been drawing attention. Sugarcane ethanol is regarded as a win-win strategy, since deforestation and water footprint level, along with nitrogen use efficiency, empowers its sustainability potential (de Oliveira Bordonal et al., 2018). Research on how to make it even greener guides the debate towards innovation fostered by public policies related to greener production practices, such as the second-generation ethanol sourced from residual biomass (de Paula, Pereira & Parmentier, 2019). However, one of the remaining grounds for criticism is the food versus fuel debate, rooted in land use. Studies show in the last decade that sugarcane cultivation rivals food crops, such as cassava, rice, potatoes and fruits. Increasing demand for fuel possibly challenges land use issues, rising concerns related to the increase in land use and food price increase (Caldarelli & Gilio, 2018). Sugarcane expansion is considered a treat for food security and small-scale farmers' livelihoods and culture (Souza et al., 2017).
4.2. Global Syndemic and food security
In the health domain, we highlight the topic of a global syndemic. Which consists of the synergy of pandemics of obesity, undernutrition and climate change with direct impacts on health and the environment. Climate change from extreme weather events, droughts and changes in agricultural production can lead to food insecurity (Swinburn et al., 2019).
Since 1980 the worldwide prevalence of overweight and obesity has doubled, affecting one-third of the population. Obesity rates increase in all ages and sexes, regardless of locality, ethnicity, or socio-economic status. However, there is a higher prevalence of obesity (target 3.4) among the elderly and women (Choi et al., 2019) which denotes a disproportionate burden on the vulnerable populations (target 1.4). In addition to the direct health effects, obesity impacts the economic burden. Comparative analysis of medical costs shows that overweight and obese people spend 32% more annually than those with average weight (Yusefzadeh, Rashidi, Rahimi, 2019).
In the Brazilian context, public food and nutrition policies and the public health system in the field of Primary Health Care contribute to articulating the development of a sustainable food system that confronts the global syndemic (Machado et al., 2021). Changes in the dietary pattern of the Brazilian population in the last three decades are characterised by the increase in the acquisition of ultra-processed foods with a predominance of in natura or minimally processed foods and processed culinary ingredients (Levy et al., 2022). The process of nutritional transition in the Brazilian population is evidenced by the time trend to increase excess weight (target 2.2) that affects adolescents, adults, elderly and pregnant women in all regions (Barancelli, Gazolla, Schneider, 2022). Chronic noncommunicable diseases (target 3.4) associated with poor diet have an economic burden on Brazil's public health system (target 3.8). In 2018, obesity, hypertension, and diabetes costs totalled US$ 890 million (Nilson et al., 2020).
Food insecurity is a severe global public health (target 3.8) problem. By 2020, the scourge of hunger will affect between 720 and 811 million. In addition, more than 3 billion faced quantitative and qualitative food access restrictions (FAO, 2021). In Brazil, data from the II National Survey on Food Insecurity context of the COVID-19 pandemic in Brazil pointed out that in 2022, more than 33 million people in hunger situation (II VIGISAN, 2022), a consequence of political and economic instability and the dismantling of public policies (Santos et al., 2021).
Recent studies indicate the relationship between food and water insecurity (Young et al., 2021). In Brazil, it was observed that in households exposed to moderate (16.5%) and severe (27.3%) levels of Food Insecurity, the occurrence of Water Insecurity was more frequent, especially those considered in food security (target 2.1) and mild food insecurity situations (target 2.2). Thus, it is verified that HI is significantly associated with AI, with potential consequences for safe access to food, the risk of foodborne diseases (ADs), physical, and mental health, nutritional status to the prevention and control of infectious diseases (Miller et al., 2021a; Miller et al., 2021b; Stoler et al., 2021; Hannah et al., 2021).
Despite progress, ensuring the human right to drinking water (target 6.1) is challenging for the 2030 Agenda. It is verified that HI is a global phenomenon, affecting as many developed countries as developing countries, neglected by their governance. In this sense, there is a growing need for measurement in different dimensions (home-individual; new information and communication technologies; and new approaches to managing complex water infrastructures (target 6.4) more inclusively and democratically (target 6.5), capable of monitoring the effectiveness of water interventions and ensuring water security (Wilson et al., 2021).
4.3. Family farming and public policy
The trend related to public food policy impacts on food security gained momentum with Brazil's constant institutional, political and economic crises. Institutional inefficiency (target 16.6) and constant shifts in policy goals explain the paradoxical situation of the existence of hunger in one of the biggest food producers in the world. The most renowned Brazilian public policy refers to the Zero Hunger program, which comprises an overarching of projects and actions. The Food Procurement Programme (PAA) and the National School Feeding Programme (PNAE) are the most extensive programs that act in a synergic way between food security and sustainable procurement (target 12.7). These policies bridge the gap between family-based food producers and consumers by fostering food acquisition locally (Wittman & Blesh, 2017). In addition to the common issues that have been jeopardising the continuity of the programs, the emergency of the COVID-19 pandemic aggravated the vulnerability of communities. Brazil, once a model for hunger eradication (target 2.1), decreased in most food security indicators (Ferreira Costa, 2021).
Trade-offs between food and energy also impact family farming in the Brazilian agricultural frontier. The agrofuel policies related to sugarcane have been a long tension point related to land-use rights. Agrofuel production rewired the land acquisition process (target 1.4) and fostered conflicts (target 16.1) between peasantry and companies, also disrupting or undermining forms of economic participation by family-based farming (target 2.3) (Fernandes, Welch & Gonçalves, 2010). Despite the longevity of this debate, academics still devote significant attention to this topic, including regional specificities for land preservation.
4.4. Specific biomes and deforestation
Brazil is a biodiversity vault that goes beyond the Amazon rainforest. Biomes such as the Cerrado (savanna-like vegetation), the Atlantic forest, the Pantanal (wetlands) and Brazilian mangroves are home to a great diversity of endemic and endangered animal and plant species (Lahsen, Bustamante & Dalla-Nora, 2016), which integrate fragile ecosystems under constant pressure from human actions. In addition, the biodiversity of these regions is an integral part of Brazil's cultural diversity and historical heritage (Bortolotto et al., 2017).
In extremely fragile ecosystems, social and environmental targets can benefit from establishing protected areas. In mangroves and coastal line areas, local populations can improve their food security by consuming local resources such as fished and naturally gathered food items (Nakamura & Hanazaki, 2017) while not destroying the environment. Nutritional gains from consumption of local resources, interlinkage food security and biodiversity conservation in a complex set of drivers that goes beyond economic factors. Hunting of local species, for instance, can posit a thin threshold between trade-offs and synergies; positive outcomes such as nutritional gains from protein consumption (target 2.1) and poverty alleviation (target 1.1) might clash with negative impacts on biodiversity conservation (target 15.1) and illegal poaching (target 15.7). Torres et al. (2021) identified that bushmeat consumption in the Amazon frontier was unrelated to wealth. In contrast, natural and cultural heritage (target 11.4) factors, such as social relations and forest cover, acted as the main drivers for hunting and consumption of local species. In this kind of context, the balance might be found in a sustainable exploration of natural resources (target 2.2).
The primary pressure on the Cerrado and Atlantic forest ecosystem comes from the expansion of the agricultural frontier of sugarcane (Granco et al., 2017) and soy production (Lima et al., 2019). The majority of sugarcane production is in the state of Sao Paulo, a geographical transition spot connecting both biomes. The externalities and trade-offs involved connecting sugarcane to the environmental dimension through water footprint (target 6.4) and deforestation (target 15.5) (Hunke et al., 2015). In addition, both cultivations are non-food related, posing a decision-making trade-off on the land use implications (target 2.4). For sugarcane, the trade-off is between clean energy (target 7.2) and food production (target 2.1); for soy involves food commodities in global markets (target 2.c).
Agricultural intensification also appears as a mitigating driver for trade-offs involving land use, food supply and biodiversity losses not only in Brazil (Garret et al., 2018) but also in other emerging markets such as India (Hinz et al., 2020). Beef production is one of climate change's main drivers (target 13.1). It is one good example of complexity in trade-offs involving different biomes within the same country and food category. Different strategies are needed for the different biomes. For instance, in the southern region, where the Pantanal and Pampa biomes are located, seasonal grazing cattle production using the local ecosystem inputs and preservation of local forage biodiversity (target 2.5) might be the best call in terms of environmental footprint. On the other hand, when it comes to Amazon and Cerrado biomes, up to the central and northern regions of the country, the intensification of agriculture (target 2.3) and the introduction of more efficient forage species can mitigate the impacts of climate change and deforestation (Dick et al., 2021).
The general call for improvement of land and soil quality through expansion of areas under sustainable, modern and productive agriculture (target 2.4) can manifest itself in different ways, as mentioned above, from the establishment of protected areas where its restoration is urgent to address specific characteristics of the biome fostering its resilience to the expansion, and/or combining innovation production methods to increase land productivity. Regardless of the pathways, the social, economic and environmental trade-off will always be present and must be accordingly weighted through evidence-based policy decision-making. Brazil is located right in the middle of this trade-off nexus when it comes to global food supply chains (target 12.2), since it is, at the same time, a biodiversity-rich scenario and holds challenging socio-economic indexes. Policies for improving governance structures, education and involvement of all stakeholders in the decision-making process (Lahsen, Bustamante & Dalla-Nora, 2016) are among the beacons to re-steering the "global food tycoon" to a sustainable food production reference (target 12.6).