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Palm oil's contribution to the United Nations sustainable development goals: outcomes of a review of socio-economic aspects

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Published 7 June 2022 © 2022 The Author(s). Published by IOP Publishing Ltd
, , Citation Maria Vincenza Chiriacò et al 2022 Environ. Res. Lett. 17 063007DOI 10.1088/1748-9326/ac6e77

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Abstract

Palm oil is both the world's most-used vegetable oil and the most criticized for its environmental impact due to the observed reduction in tropical forest areas for its cultivation over the past decades. There is, however, very little discussion on the socio-economic implications associated with the production of palm oil. To contribute to a more informed debate, we conducted an in-depth review of the existing literature addressing the various socio-economic aspects of the production of palm oil, outlining its contribution to the achievement of the United Nations sustainable development goals (SDGs). The outcomes, findings and conclusions from 82 studies, published from 2010 onward, were considered as positive, negative, neutral or varied, and sometimes even contradicting, with regard to the contribution of palm cultivation and/or oil production to the achievement of a set of eight SDGs, selected to be those most related to socio-economic development, differentiating when possible between sustainable and conventional production. The results show that it is difficult to draw uniform views, highlighting the nuances and varied facets of the contribution of palm oil to the eight SDGs, some of which are inevitably interconnected. In general, it emerges that palm oil plays a crucial role in boosting the economy and livelihoods of local communities in many developing producer countries, substantially contributing to poverty reduction and to food security. However, the expansion of oil palm plantations has, in some cases, exacerbated social inequalities, and the economic growth generated by the palm oil production chain is not always accompanied by decent working conditions. Against this backdrop, the achievement of some SDGs is often facilitated by the implementation of sustainability certification schemes that play a key role in improving the socio-economic and environmental performance of palm oil production. This leads enhanced socio-economic livelihoods for the people living in the production areas in terms of working conditions, infrastructure, services and wages, with a consequent reduction of poverty rates, an increase in education quality, as well as better access to food and healthcare systems.

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1. Background

Palm oil is the most widely used vegetable oil in the world, accounting for more than 35% of all vegetable oil production, followed by soybean oil (28%), rapeseed oil (12%) and sunflower oil (9%) (FAOSTAT 2021). From the second half of the twentieth century onwards, there has been an exponential increase in the production of palm oil, which has proven to be very versatile (Qaim et al 2020); so much so that it has become a common ingredient in many food products, such as margarine, biscuits, bread, cakes, chocolate, ice cream and non-food products such as detergents and cosmetics (Shimizu and Desrochers 2012, Oosterveer 2014, Kushairi et al 2017, Pacheco et al 2017). Palm oil has also historically been used as a lubricant for machinery (Shimizu and Desrochers 2012, Budidarsono et al 2013) and its use as a biofuel in the energy sector has been growing particularly rapidly (Silalertruksa et al 2012, Ofosu-Budu and Sarpong 2013, Khatun et al 2017, Muhammad et al 2019).

Today, palm oil is at the same time the world's most-used vegetable oil and the most criticized: the issue of controversy that led palm oil at the centre of the public and scientific debate in the last years (Rist et al 2010, Cramb and Curry 2012, Azhar et al 2017) is its environmental impact and particularly the link between its cultivation and the reduction in tropical forest areas over the past decades (Obidzinski et al 2012, Edwards 2015, Moreno-Peñaranda et al 2015, Pacheco et al 2017, Sharma et al 2019, Lee et al 2020). Indeed, in recent decades, the expansion of oil palm cultivation has led to the reduction of vast areas of tropical forest and the drainage of some natural peatlands, resulting in the loss of significant forest carbon stocks, increased greenhouse gas emissions, the destruction of important natural habitats, threats to biodiversity and the triggering of soil erosion processes (Dradjat 2012, Schrier-Uijl et al 2013, Khatun et al 2017, Pacheco et al 2017, Lee et al 2020).

Albeit that the concept of sustainability is conceived of in terms of three dimensions–environmental, economic and social–the debate on palm oil focuses mostly on its effects on the environment and ecosystem services and there is very little discussion on the socio-economic impacts associated with the production of palm oil. Therefore, the objective of this paper is to contribute to a more informed and comprehensive debate on palm oil, considering in particular the less investigated and discussed socio-economic aspects of palm oil production. To this aim, we conducted a systematic review of the relevant existing literature that has investigated the socio-economic implications of palm oil, differentiating, when possible, the effects of sustainable and conventional palm oil. The outcomes, findings and conclusions from the selected studies were then categorized by the authors in terms of contribution to the achievement of a set of eight—selected considering those most related to the socio-economic development—out of the 17 United Nations sustainable development goals (SDGs) of the 2030 Agenda for Sustainable Development (UN 2015) adopted by UN Member States in 2015 as a plan for the peace and prosperity of the people and the planet.

The review presented in this paper offers a quite novel overview of the socio-economic aspects related to palm oil production, addressing for the first time the link with the SDGs, since only a few similar reviews exist in the literature and they are not directly associated with SDGs. Lee et al (2020) discuss the environmental and development goals that can be achieved with certified palm oil production in Indonesia and Purnomo et al (2018) present research on the development of indicators that can advise to the achievement of SDGs. However, neither of them provide a comprehensive assessment of the general contribution of palm oil to the progress towards the SDGs most related to socio-economic development. A recent review from Qaim et al (2020) analyses the implications of the growth of palm oil production in the last few years from environmental, economic and social perspectives, considering important aspects such as rainforest protection, income and land property rights, smallholders and social inclusion, and sustainability certification. Despite the comprehensive discussion provided, the study does not report any specific reference or direct link in terms of contribution to the achievement of SDGs. Meijaard et al (2020) reviewed the environmental impacts of palm oil and linked their findings and results with SDGs. However, in another study, Meijaard and Sheil (2019) highlighted that a more complete assessment of palm oil effects should consider not just the environmental aspects but also the extent to which it can benefit people, considering the influence on poverty, hunger and all the factors included under the 17 SDGs.

1.1. Trends in palm oil production

One of the characteristics of oil palm plantations is their high yield in terms of amount of oil produced per unit of cultivated area, with two different types of products that can be extracted from the fruit of oil palm: palm oil from the fruit and, in smaller quantities (about 10%), palm kernel oil from the seeds of the fruit, with an average yield of 3–4 tonnes per hectare of palm oil and 0.5 tonnes per hectare of palm kernel oil (Azhar et al 2017, FAOSTAT 2021). This is up to 10 times more than any other commonly used vegetable oil (Khatun et al 2017), thereby requiring less land than other oil crops for the same amount of product obtained. This characteristic is confirmed by Food and Agriculture Organization Corporate Statistical Database (FAOSTAT) data that indicate for 2019 that although oil palm cultivation accounts for over 35% of global vegetable oil production, it occupies about 28 million hectares, which is less than 10% of the land used for vegetable oil production worldwide (FAOSTAT 2021).

The annual global production of palm oil in 2018 was around 80 million tonnes—this includes the production of both palm oil (90%) and palm kernel oil (10%)—an increase of +55% compared to production in 2010 (51.3 million tonnes) (FAOSTAT 2021). Palm oil production and use is, therefore, growing steadily (Khatun et al 2017, FAOSTAT 2021), and is expected to increase even further (Corley 2009) given the steady increase in demand for food and energy from the world's population, which is forecast to top about 10 billion people by 2050 (IFAD 2014, FAO 2015). Currently, Indonesia and Malaysia are the largest producers of palm oil, accounting for about 88% of global production with 40.6 and 19.5 million tonnes, respectively, in 2018 (FAOSTAT 2021), and host the majority of oil palm plantations with 14.7 and 5.2 Mha, respectively, although other tropical areas, including Thailand, Central and South America, and West Africa, are recently and rapidly expanding their oil palm plantations.

The increasing demand for palm oil from the international market, together with the growing public attention as to its impact on the environment and society, has prompted the various players in the palm oil production chain to raise awareness regarding the need to engage in more sustainable production methods than those conventionally used. This new awareness has led to the development of a series of certification schemes and protocols, which have been expanded over the years to include both environmental and socio-economic principles and criteria for the sustainable production of palm oil. Among the high number of standards and protocols covering sustainable agri-food production or the protection of habitats and biodiversity, some can be specifically applied to sustainable palm oil production (Yaap and Paoli 2014, McInnes 2017, Schlösser and Walter 2020), addressing its environmental and socio-economic aspects, either directly or indirectly (table 1).

Table 1. Selection of existing standards applicable to sustainable palm oil production.

StandardsDescription
Roundtable on Sustainable Palm Oil (RSPO)A non-profit, multi-stakeholder initiative launched in 2004 with the aim of promoting the growth and use of sustainable palm oil products through credible global standards and the involvement of the stakeholders, including producers, dealers, consumers, retailers, banks and investors, and environmental and social non-governmental organisations. The global certification standard for sustainable palm oil production, RSPO, provides for operations in the field and supply chain management in compliance with regulations—with low environmental impact—that are economically and socially advantageous to the workers and local communities. Updated in 2018, the RSPO principles and criteria are based on seven principles and 40 criteria (with respective indicators and guidelines) organised into three impact areas (prosperity, people and planet).
Indonesian Sustainable Palm Oil (ISPO)Mandatory Indonesian certification standard for the production of sustainable palm oil, drawn up by the Government of Indonesia in 2011. ISPO criteria are aligned with existing legal and regulatory requirements in Indonesia; this is why it is also referred to as the 'standard of legality' for palm oil. ISPO provides for the application of seven principles, 28 criteria and 15 sub-criteria, including a plantation licensing and management system, compliance with technical guidelines for cultivation and processing, environmental management and monitoring, respect for the conditions of the workers and local communities, the strengthening of economic activities in the communities, and the development of a sustainable economy.
Malaysian Sustainable Palm Oil (MSPO)Mandatory Malaysian certification standard for sustainable palm oil production, drawn up by the Government of Malaysia in 2013. The MSPO criteria are aligned with existing legal and regulatory requirements in Malaysia. MSPO contains seven principles, each with specific criteria and indicators, based on the three pillars of sustainability, which guarantee economically viable, socially acceptable and environmentally friendly palm oil production.
Palm Oil Innovation Group (POIG)A 2013 multi-stakeholder initiative that builds on the RSPO standard and promotes the adoption by key players throughout the palm oil production chain of more stringent and innovative sustainable and responsible practices in terms of environmental responsibility, partnership with local communities, protection of workers' rights and corporate and product integrity.
Rainforest Alliance: Sustainable Agriculture Standard (SAS)Certification programme for producers who engage in sustainable agricultural production and responsible supply chains, including that of palm oil. It is based on five principles, with respective criteria, that provide for the drafting and application of a business and supply chain management plan aimed at preserving biodiversity and natural resources, improving the livelihoods and well-being of workers and their families, including appropriate working conditions, wages, healthcare, safety and the protection of relations with local communities.
Sustainable Agriculture Network (SAN)International network of non-governmental organisations (NGOs) focused on helping farmers, workers and rural communities pursue their sustainability agenda in a practical and efficient manner. The network works alongside the Rainforest Alliance, managing a global system to certify the sustainable agricultural production of responsible farm businesses and agricultural supply chains, including that of palm oil.
Roundtable on Sustainable Biomaterials (RSB)Global, independent multi-stakeholder organisation set up in 2011 with the aim of encouraging the sustainable production of biofuels (including biodiesel from oil palm processing) and other biomaterials through sustainable practices, certification and cooperation partnerships. It is based on the application of a standard with 12 fundamental principles, each of which is supported by a variable number of criteria, requirements and indicators, covering four areas (legal, social, environment and management).
High Carbon Stocks Approach (HCS)An approach designed to enable farm businesses in various sectors, including the oil palm sector, to fulfil their commitments against deforestation, both at the production stage in the field, and throughout the supply chain. It is not a standalone certification scheme and most palm oil companies that have applied the HCS approach have also subscribed to RSPO.
International Standard for Carbon Certification (ISCC)Certification system oriented towards the reduction of greenhouse gas emissions, sustainable land use, protection of the biosphere and social sustainability, through the application of a standard all along the supply chain in three key areas: energy, industrial applications, food and feed.

According to RSPO data (RSPO 2021)—one of the most comprehensive certification schemes as reported by a number of studies that analyse and compare the main sustainability standards for agricultural production (Yaap and Paoli 2014, McInnes 2017, Schlösser and Walter 2020)—currently 4.36 million hectares of the 28 million cultivated with oil palm worldwide are certified as sustainable, accounting for a total of 17.6 million tonnes of palm oil and corresponding to 19% of the global production of palm oil.

2. Methods

The systematic review of the socio-economic aspects related to palm oil production presented in this study is based on recent studies that discuss one or more socio-economic implications of palm oil or make explicit reference to SDGs, possibly differentiating between sustainable and conventional palm oil production. With the aim to include the most recent studies, the authors decided to include in the review papers published from 2010 up to 2020, with the only exception of one study (Susila 2004) that was mentioned as particularly relevant in many studies. Although sustainability encompasses three environmental, economic and social dimensions, according to the aim of this study to address specifically, the socio-economic dimensions of palm oil, being the environmental aspects of palm oil production widely investigated in the literature, a set of eight SDGs was selected considering those most related to the socio-economic development—according to the authors' judgment and as suggested also by Fonseca et al (2020) and Niaz (2021):

  • SDG 1: no poverty
  • SDG 2: zero hunger
  • SDG 3: good health and well-being
  • SDG 4: quality education
  • SDG 5: gender equality
  • SDG 6: clean water and sanitation
  • SDG 8: decent work and economic growth
  • SDG 10: reduced inequality

The literature search was performed in Google Scholar, using search terms in various combinations. Specifically, the keywords palm oil production and oil palm cultivation were crossed with the general terms social impact, economic impact, sustainability, SDGs and with the following specific terms to facilitate the attribution of the studies to each SDG, with the same study attributable to one or more SDGs if containing the associated specific terms:

  • SDG 1: poverty, income
  • SDG 2: hunger, food, food security
  • SDG 3: health, well-being
  • SDG 4: education, school, student
  • SDG 5: gender, women
  • SDG 6: water, sanitation
  • SDG 8: work, workers, economic growth, employment, salary
  • SDG 10: equity, inequality, social conflict, discrimination, vulnerable

Albeit the triple environmental–economic–social dimension of sustainability, given the well-defined focus of this paper to address specifically only the socio-economic dimensions of palm oil, the terms related to the environmental impact and to the environmental sustainability were intentionally not included in the literature search, being the environmental concerns already extensively discussed in the literature.

The resulting papers that were accessible to the authors (e.g. open access or subscribed journals by the institution of the authors) were fully read and then screened on the basis of the exclusion criteria listed below. The papers excluded:

  • provide a focus on too specific aspects thus not allowing an assessment of impacts against any of the selected SDGs, such as papers dealing with particular food products containing palm oil (Cova and D'Antone 2016), educational campaigns (Ruggeri and Samoggia 2018), incentive systems (Cramb 2013) or application of specific practices and innovations in the value chain (Ayinde et al 2012, Osei-Amponsah et al 2012, Ayawari et al 2018);
  • although dealing with the SDGs of interest, focus their impact analysis on other aspects, e.g. governance and policy strategies (Fuchs et al 2011, Pesqueira and Glasbergen 2013, van der Enden 2013, Köhne 2014, MacDonald 2020) or environmental aspects (Gilbert 2012, Silalertruksa et al 2017);
  • provide a comparative analysis of multiple vegetable oils, including palm oil, but not allowing to assess specifically the palm oil effects in absolute terms (German and Schoneveld 2011, Fonjong and Gyapong 2020).

Out of the 105 published studies that were analysed (full list in the supplementary information available online at stacks.iop.org/ERL/17/063007/mmedia), 82 were eligible to be included for the review according to the exclusion criteria, differentiated in scientific original articles (57), scientific reviews (9) and working papers (16). A great part of the 82 selected studies refers to specific production areas, such as Southeast Asia, in particular Indonesia and Malaysia (55), Africa (12) and Latin America (4), while others (11) analyse the socio-economic aspects of palm oil production worldwide (table 2). Additionally, a number of studies analyses the socio-economic aspects of palm oil production certified as sustainable with reference to one of the certification schemes listed in table 1 (18) or make comparisons between sustainable and conventional production (12). The remainder of the studies refers to conventional production or does not specify the production method (52) (table 3).

Table 2. List of studies analysed, with reference to geographical areas.

Geographical areaStudies
Southeast Asia (55)Susila 2004, McCarthy and Cramb 2009, Feintrenie et al 2010, Rist et al 2010, Dayang Norwana et al 2011, Syahza et al 2011, Budidarsono et al 2012, Cramb and Curry 2012, Dradjat 2012, White and White 2012, Majid Cooke 2012, Obidzinski et al 2012, Shimizu and Desrochers 2012, Silalertruksa et al 2012, Varkkey 2012, Budidarsono et al 2013, Manik et al 2013, Schrier-Uijl et al 2013, Sinaga 2013, Ludin et al 2014, Kamalrudin and Abdullah 2014, Yaap and Paoli 2014, Alam et al 2015, Alwarritzi et al 2015, Edwards 2015, Comte et al 2015, Li 2015, Moreno-Peñaranda et al 2015, Otieno et al 2016, UNICEF 2016, Elmhirst et al 2017a, Elmhirst et al 2017b, Jelsma et al 2017, Kushairi et al 2017, Hidayat et al 2018, Dib et al 2018, Edwards 2018, Li 2018, Morgans et al 2018, Nambiappan et al 2018, Papilo et al 2018, Purnomo et al 2018, de Vos and Delabre 2018, Acosta and Curt 2019, Adiprasetyo et al 2019, Foong et al 2019, Jensen et al 2019, Muhammad et al 2019, Santika et al 2019, Sharma et al 2019, Sibhatu 2019, Lee et al 2020, Purnomo et al 2020, Santika et al 2020, Sitepu et al 2020.
Africa (12)Ayodele 2010, Ibitoye et al 2011, Hoyle and Levang 2012, Ofosu-Budu and Sarpong 2013, Nkongho et al 2014, Ohimain et al 2014, Adebo et al 2015, Adesiji et al 2016, Bassey 2016, Ahmed et al 2019, Balde et al 2019, Etuah et al 2020.
Latin America (4)Mingorría et al 2014, Castellanos-Navarrete et al 2019, Grepalma 2020, Furumo et al 2020.
Global production (11)Obire and Putheti 2010, Persey et al 2011, Oosterveer 2014, Potter 2015, Pirker et al 2016, Azhar et al 2017, Khatun et al 2017, Pacheco et al 2017, Meijaard and Sheil 2019, Pye 2019, Qaim et al 2020.

Table 3. List of studies analysed, with reference to the type of production.

Type of productionStudies
Sustainable production (18)Persey et al 2011, Schrier-Uijl et al 2013, Kamalrudin and Abdullah 2014, Ludin et al 2014, Oosterveer 2014, Yaap and Paoli 2014, Moreno-Peñaranda et al 2015, Khatun et al 2017, Kushairi et al 2017, Hidayat et al 2018, Papilo et al 2018, Purnomo et al 2018, Foong et al 2019, Grepalma 2020, Meijaard and Sheil 2019, Pye 2019, Santika et al 2020, Sitepu et al 2020.
Comparison between sustainable and conventional production (12)Cramb and Curry 2012, Potter 2015, Azhar et al 2017, Elmhirst et al 2017a, Jelsma et al 2017, Morgans et al 2018, Adiprasetyo et al 2019, Santika et al 2019, Sharma et al 2019, Furumo et al 2020, Lee et al 2020, Purnomo et al 2020.

It is worth noting that all the reviewed studies that were considered as addressing 'sustainable' palm oil make explicit reference to certified sustainable production and, conversely, those studies addressing 'conventional' palm oil deal with non-certified production. It could be that some studies deal with palm oil production from smallholders who despite applying sustainable practices cannot afford the costs to obtain a certification, thus they are not identified and acknowledged as being 'sustainable', albeit simplified approaches for the certification of sustainable palm oil for small independent farmers have been recently developed (Meijaard and Sheil 2019, Yap et al 2021). However, when sustainable palm oil is mentioned in this study, it refers to certified sustainable production methods that respect the environmental and socio-economic principles and criteria set by recognized standards and protocols for the sustainable production of palm oil (see table 1).

The outcomes, findings and conclusions from the selected studies were collected in a database and categorized as markedly positive, negative or neutral with regard to the contribution of palm oil to the achievement of the eight selected SDGs (table 4).

Table 4. List of studies analysed, broken down according to SDGs.

 ArticlesScientific reviewsWorking papers
SDG 1 (n = 41) Susila 2004, McCarthy and Cramb 2009, Rist et al 2010, Syahza et al 2011, Cramb and Curry 2012, Sinaga 2013, Ohimain et al 2014, Oosterveer 2014, Kamalrudin & Abudallah 2014, Alwarritzi et al 2015, Adesiji et al 2016, Azhar et al 2017, Jelsma et al 2017, Ahmed et al 2019, Castellanos-Navarrete et al 2019, Meijaard and Sheil 2019, Muhammad et al 2019, Pye 2019, Santika et al 2019, Etuah et al 2020, Qaim et al 2020, Santika et al 2020. (n = 22) Obire and Putheti 2010, Persey et al 2011, Budidarsono et al 2012, Schrier-Uijl et al 2013, Potter 2015, Morgans et al 2018. (n = 6) Ayodele 2010, Feintrenie et al 2010, Dayang Norwana et al 2011, Dradjat 2012, Ofosu-Budu and Sarpong 2013, Nkongho et al 2014, Edwards 2015, Li 2015, Pacheco et al 2017, Edwards 2018, Li 2018, Adiprasetyo et al 2019, Grepalma 2020. (n = 13)
SDG 2 (n = 27) White and White 2012, Budidarsono et al 2013, Manik et al 2013, Sinaga 2013, Mingorría et al 2014, Alwarritzi et al 2015, Bassey 2016, Azhar et al 2017, Khatun et al 2017, Ahmed et al 2019, Balde et al 2019, Castellanos-Navarrete et al 2019, Jensen et al 2019, Meijaard and Sheil 2019, Santika et al 2019, Sharma et al 2019, Sibhatu 2019, Qaim et al 2020, Santika et al 2020. (n = 19) Budidarsono et al 2012. (n = 1) Ayodele 2010, Li 2015, UNICEF 2016, Elmhirst et al 2017a, Pacheco et al 2017, Li 2018, Grepalma 2020. (n = 7)
SDG 3 (n =30) Syahza et al 2011, Varkkey 2012, Budidarsono et al 2013, Manik et al 2013, Mingorría et al 2014, Adebo et al 2015, Alwarritzi et al 2015, Moreno-Peñaranda et al 2015, Elmhirst et al 2017b, Nambiappan et al 2018, Acosta and Curt 2019, Ahmed et al 2019, Castellanos-Navarrete et al 2019, Jensen et al 2019, Santika et al 2019, Sibhatu 2019, Lee et al 2020, Qaim et al 2020, Santika et al 2020. (n =19)Shimizu and Desrochers 2012, Schrier-Uijl et al 2013, Yaap and Paoli 2014, Potter 2015, Kushairi et al 2017, Morgans et al 2018. (n = 6) Feintrenie et al 2010, Elmhirst et al 2017a, Pacheco et al 2017, Li 2018, Grepalma 2020. (n = 5)
SDG 4 (n = 20) Obidzinski et al 2012, Budidarsono et al 2013, Alwarritzi et al 2015, Adesiji et al 2016, Acosta and Curt 2019, Santika et al 2019, Furumo et al 2020, Lee et al 2020, Qaim et al 2020, Santika et al 2020, Sitepu et al 2020. (n = 11)Budidarsono et al 2012, Schrier-Uijl et al 2013, Yaap and Paoli 2014. (n = 3) Feintrenie et al 2010, Dayang Norwana et al 2011, UNICEF 2016, Pacheco et al 2017, Li 2018, Grepalma 2020. (n = 6)
SDG 5 (n = 16) Ibitoye et al 2011, White and White 2012, Adebo et al 2015, Moreno-Peñaranda et al 2015, Adesiji et al 2016, Bassey 2016, Elmhirst et al 2017b, de Vos and Delabre 2018, Castellanos-Navarrete et al 2019, Etuah et al 2020. (n = 10)Yaap and Paoli 2014. (n = 1) Li 2015, UNICEF 2016; Elmhirst et al 2017a, Li 2018, Grepalma 2020. (n = 5)
SDG 6 (n = 20) Rist et al 2010, Cramb and Curry 2012, Obidzinski et al 2012, Manik et al 2013, Comte et al 2015, Moreno-Peñaranda et al 2015, Nambiappan et al 2018, Foong et al 2019, Sharma et al 2019, Furumo et al 2020, Lee et al 2020, Santika et al 2020. (n = 12)Yaap and Paoli 2014. (n = 1) Dradjat 2012, Li 2015, UNICEF 2016, Elmhirst et al 2017a, Pacheco et al 2017, Li 2018, Grepalma 2020. (n = 7)
SDG 8 (n = 59) Susila 2004, Rist et al 2010, Ibitoye et al 2011, Cramb and Curry 2012, Majid Cooke 2012, Obidzinski et al 2012, Silalertruksa et al 2012, Budidarsono et al 2013, Manik et al 2013, Sinaga 2013, Kamalrudin and Abdullah 2014, Ludin et al 2014, Mingorría et al 2014, Ohimain et al 2014, Alam et al 2015, Alwarritzi et al 2015, Moreno-Peñaranda et al 2015, Adesiji et al 2016, Bassey 2016, Otieno et al 2016, Pirker et al 2016, Elmhirst et al 2017b, Dib et al 2018, Nambiappan et al 2018, Papilo et al 2018, Purnomo et al 2018, Acosta and Curt 2019, Balde et al 2019, Castellanos-Navarrete et al 2019, Muhammad et al 2019, Pye 2019, Santika et al 2019, Sharma et al 2019, Furumo et al 2020, Purnomo et al 2020, Qaim et al 2020, Santika et al 2020, Sitepu et al 2020. (n = 38)Obire and Putheti 2010, Persey et al 2011, Shimizu and Desrochers 2012, Schrier-Uijl et al 2013, Yaap and Paoli 2014, Potter 2015, Morgans et al 2018. (n = 7) Ayodele 2010, Feintrenie et al 2010, Dayang Norwana et al 2011, Dradjat 2012, Hoyle and Levang 2012, Ofosu-Budu and Sarpong 2013, Nkongho et al 2014, Li 2015, Pacheco et al 2017, Edwards 2018, Li 2018; Elmhirst et al 2017a, Adiprasetyo et al 2019, Grepalma 2020. (n = 14)
SDG 10 (n = 30) Susila 2004, McCarthy and Cramb 2009, Syahza et al 2011, Cramb and Curry 2012, Manik et al 2013, Mingorría et al 2014, Oosterveer 2014, Alam et al 2015, Bassey 2016, Elmhirst et al 2017b, Jelsma et al 2017, Dib et al 2018, Hidayat et al 2018, Acosta and Curt 2019, Castellanos-Navarrete et al 2019, Muhammad et al 2019, Santika et al 2019, Qaim et al 2020. (n = 18)Persey et al 2011, Yaap and Paoli 2014. (n = 2) Feintrenie et al 2010, Dayang Norwana et al 2011, Dradjat 2012, Hoyle and Levang 2012, Nkongho et al 2014, Elmhirst et al 2017a, Pacheco et al 2017, Li 2018, Adiprasetyo et al 2019, Grepalma 2020. (n = 10)

Each study was categorized with regard to the contribution of the palm cultivation and/or oil production to the achievement of a specific SDG as follows:

  • markedly positive or negative when it clearly provides a positive or negative qualitative (and sometimes quantitative) evaluation highlighting benefits or detrimental effects over specific issues related to the SDGs considered;
  • neutral when it deals with the considered SDGs with varied and sometimes even contradictory points of view, or reporting a trade-off between positive and negative aspects with no relevance of one aspect over the other.

Although all the 17 SDGs are conceived as an integrated approach for the sustainable development, this analysis addresses individually the eight selected SDGs, highlighting when appropriate the interconnection among them, with the aim to provide an overview on which are the most and the less-investigated topics in relation to palm oil and for which ones positive or negative impacts are described in the literature.

3. Review results and discussion

3.1. SDG 1: no poverty

The literature review showed that many studies agree that oil palm cultivation contributes positively to the socio-economic development of local communities, irrespective of the country of production or the approach used, with a substantially positive impact on poverty reduction and economic growth in rural areas (Susila 2004, Obire and Putheti 2010, Schrier-Uijl et al 2013, Kamalrudin and Abdullah 2014, Edwards 2018, Ahmed et al 2019). The effects of poverty reduction and economic growth are even greater for small producers who also manage to grow other crops in association with oil palm (Feintrenie et al 2010, Fu et al 2010, Kremen et al 2012, Azhar et al 2017).

In developing countries, the poverty rate of communities engaged in oil palm cultivation tends to be lower than the national average (Etuah et al 2020), with examples in Indonesia (Susila 2004, Dradjat 2012, Alwarritzi et al 2015, Edwards 2018, Etuah et al 2020) and Nigeria (Ayodele 2010, Adesiji et al 2016, Etuah et al 2020). One study in particular (Edwards 2015) shows how a 10% increase in the land area dedicated to oil palm cultivation produces a 10% reduction in the poverty rate, leading to a reduction in the poverty gap between various social classes (Edwards 2015, Pacheco et al 2017), with short-term poverty reduction effects being greater on large-scale plantations than on small-scale ones (Edwards 2015). Edwards (2019) reports that about 2.6 million Indonesians living in rural areas have been lifted out of poverty in this century thanks to the economy linked to palm oil production (Meijaard and Sheil 2019). Numerous initiatives incentivizing oil palm cultivation are promoted locally by governments, especially in Asia (Indonesia, Malaysia, Thailand, etc) and sub-Saharan Africa (Ghana, Nigeria, Cameroon, Côte d'Ivoire, Benin, etc), as a key tool to alleviate poverty, particularly in local communities in rural areas (Susila 2004, Rist et al 2010, Syahza et al 2011, Ofosu-Budu and Sarpong 2013, Sinaga 2013, Nkongho et al 2014, Oosterveer 2014, Potter 2015, Pirker et al 2016). In many developing countries, oil palm is considered a highly profitable crop—it is, in fact, defined as a cash crop since it is grown mainly to be sold for profit, as opposed to staple crops intended as subsistence crops that are grown as food mainly for the producers' family or to feed their livestock—outstripping any other crop in terms of productivity and labour required (Feintrenie et al 2010, Rist et al 2010, Harianto 2019). Oil palm can be considered the most efficient oil crop since it is able to produce the same volume of vegetable oil on less than 20% of the area required for other oil crops, such as soybeans, rapeseed and sunflowers (Persey et al 2011, Meijaard et al 2020). Moreover, from the labour resource perspective, its cultivation only requires, on average, 0.2 man-years per hectare (Corley and Tinker 2016, Jelsma et al 2017).

What makes palm oil production one of the most desirable and accessible sources of income, with a positive impact on socio-economic development and poverty reduction, is its higher profitability and its low labour intensity (Persey et al 2011, Jelsma et al 2017, Grepalma 2020). Some studies have shown that oil palm farmers in Guinea have more stable incomes than farmers who do not grow oil palm or other cash crops (Balde et al 2019, Qaim et al 2020); furthermore, smallholders whose main source of income comes from oil palm cultivation have better financial and well-being indicators, as well as lower malnutrition rates than smallholders who do not cultivate oil palm (Dayang Norwana et al 2011, Budidarsono et al 2012).

Nevertheless, some publications underline both positive and negative effects (McCarthy and Cramb 2009, Cramb and Curry 2012, Schrier-Uijl et al 2013, Li 2015, 2018, Meijaard and Sheil 2019, Santika et al 2019, 2020). Although oil palm cultivation has produced positive economic returns, good employment levels and a general improvement in access to social services for smallholders and their families (Dayang Norwana et al 2011, Schrier-Uijl et al 2013, Ohimain et al 2014, Muhammad et al 2019), land-use change due to the expansion of palm oil, particularly for biofuel production in Malaysia, has prompted many local communities and ethnic groups to move away from their traditional lifestyles that were historically dependent on the natural resources and ecosystem services provided by natural forests (Dayang Norwana et al 2011). In particular, one study (Santika et al 2019) shows that the social impacts of oil palm plantations cannot be uniformly defined, but they are highly dependent on a number of variables, such as site-specific characteristics and socio-economic conditions of local communities prior to the start of cultivation (Meijaard and Sheil 2019, Santika et al 2019). Specifically, communities engaged in oil palm cultivation located in villages with low forest cover, accustomed to purchasing subsistence goods on the market, improved their socio-economic well-being through the development of plantations, compared to villages without oil palm (Santika et al 2019). The opposite case was observed in plantations developed in remote villages with higher forest cover, where the livelihoods of the local communities depended on direct cultivation or the utilization of forest products and services. These communities were forced into a change in their lifestyle as opposed to neighbouring communities that had not engaged in oil palm cultivation (Santika et al 2019, 2020). In general, the most consolidated, long-established communities in the area tend to resist the temptation to abandon traditional practices and culture in exchange for the stable income that palm oil production can provide, since land-use change in favour of palm oil plantations raises concerns especially with regard to maintaining land ownership and security in the land regulation system (Dayang Norwana et al 2011). One study points out that small farmers risk being impoverished by having to sell their land, which may be required for oil palm expansion. For this reason, smallholders should be supported by national legislation (Rist et al 2010, Nkongho et al 2014) through the development of a system that incentivizes and regulates the renting rather than the sale of land (Rist et al 2010).

The positive or negative impact of oil palm cultivation also depends on the social groups involved. The social and economic benefits of oil palm are usually limited to particular social groups, including, for example, smallholders who add oil palm to their farming systems, thereby diversifying the crop systems (Li 2015). Different effects in social and economic terms can also be produced depending on the relationship between the smallholders and the large companies managing the oil palm plantations (Castellanos-Navarrete et al 2019). For example, oil palm smallholders (plots averaging 2 ha) linked to large companies by supply contracts are more vulnerable to impoverishment, mainly due to the low income they receive, which, in many cases, is not sufficient to cover farm management costs and basic household expenses (Li 2018). As a result, these smallholders run the risk of losing their land and hence the ability to sustain their livelihood, and this, in turn, leads to economic and social decline (Cramb and Curry 2012, Li 2015, Cramb and McCarthy 2016). In contrast, oil palm cultivation managed by independent smallholders (ISHs) is more profitable than the above-described option, although it requires a significant initial capital outlay. It should, however, be taken into account that the minimum size of a monoculture plot should be 6 ha to guarantee productivity and meet family needs (Li 2018).

Adiprasetyo et al (2019) showed that, in general, perceived economic and environmental benefits are greater for farmers who adopt sustainable palm oil production than for conventional farmers. Specifically, an analysis carried out in Kalimantan (Indonesia) shows that the application of RSPO certification does not bring about a reduction in poverty but could be related to a deceleration in the growth of poverty rates (Morgans et al 2018). According to Azhar et al (2017), most of the certified sustainable palm oil in global markets comes from large plantations and only a small part from smallholders; this is mainly due to the high costs of certification, which are not always offset by higher selling prices. As a result, although smallholders apply traditional practices that are often more biodiversity-friendly, they are not identified and acknowledged as being 'sustainable'. Some certification schemes (RSPO and MSPO) are seeking to make certification more accessible for smallholders (Meijaard and Sheil 2019, Yap et al 2021) with the introduction in 2019 of a specific standard (RSPO ISH standard) that aims towards greater inclusion of smallholders in the RSPO certification system through a simplified approach for the production of sustainable palm oil also by small independent farmers.

3.2. SDG 2: zero hunger

Assessing the effects of palm oil production in relation to SDG 2 is a particularly important issue given the fact that current estimates show that almost 8.9% of the world's population (690 million people) suffer from hunger and malnutrition (FAO 2020) and that the majority of the world's undernourished population is in Asia (381 million) and Africa (250 million), which are the countries with the most oil palm cultivations.

Oil palm is considered a primary crop for many countries from an economic perspective, while the effects on food security can be positive or negative (Santika et al 2019, 2020). Some studies maintain that the presence of oil palm crops helps to guarantee food security (Ayodele 2010, Khatun et al 2017) and alleviate malnutrition (Budidarsono et al 2012, Khatun et al 2017). Palm oil is also a key element in the diet of many local populations. An example is Thailand where it accounts for approx. 75% of edible oil energy intake (Kosulwat et al 2006, Jensen et al 2019) thus representing a fundamental commodity for food security (Rewtarkulpaiboon 2015, Khatun et al 2017, Jensen et al 2019) due to the improvement in calorie intake deriving from its consumption. Moreover, palm oil contributes also to the improvement in the nutrition of local populations as a result of rising incomes, prompting increased spending on food, which has effectively also weakened the role of subsistence food production (Sibhatu and Qaim 2018, Sibhatu 2019, Qaim et al 2020). According to a series of studies carried out in Southeast Asia, earnings from oil palm cultivation contribute to improved food security in smallholder households by providing the families with greater economic means to purchase food (Feintrenie et al 2010, Rist et al 2010, Cramb and Curry 2012, Obidzinski et al 2012, Sibhatu 2019, Qaim et al 2020). Also, in Africa, studies in Guinea (Balde et al 2019, Qaim et al 2020) and Ghana (Ahmed et al 2019, Qaim et al 2020) report that smallholders cultivating oil palm have greater food security than those who do not, due to higher incomes that enable them to spend more on food purchases.

However, the positive effects of oil palm cultivation in terms of increased food security are particularly good for small independent farmers who have the opportunity to combine oil palm with other crops including rice, rubber and fresh vegetables in a sustainable intercropping system (Fu et al 2010, Kremen et al 2012, Li 2015, 2018, Azhar et al 2017, Grepalma 2020), thereby ensuring a varied diet and direct access to different types of food. In contrast, smallholders who adopt the monoculture oil palm system are forced to rely on the market for food purchases, abandoning subsistence farming and consequently generating increased household expenditure for the procurement of food, leading to a drop in food security for the whole family (Sinaga 2013, Alwarritzi et al 2015). A study conducted in Indonesian villages showed that where oil palm is the main source of income, malnutrition rates are lower than in villages where it is not cultivated (Budidarsono et al 2012). However, increased income does not always lead to better levels of food security, which also depends on many other factors, such as the availability of food or the efficiency of markets (Mingorría et al 2014, Alwarritzi et al 2015, Pacheco et al 2017, Elmhirst et al 2017a, Hamann 2018, Castellanos-Navarrete et al 2019).

Furthermore, while in some cases the production of palm oil improves the socio-economic conditions of smallholders and hence their food security and access to food at the local level, it could also pose a food security problem, mainly due to the risk of entire agricultural areas being converted into monoculture oil palm plantations (Pacheco et al 2017, Sharma et al 2019). A possible solution could be sustainable intensification as a compromise to avoid further expansion of oil palm in the future (Manik et al 2013, Elmhirst et al 2017b, Sharma et al 2019). Along the same lines, some studies highlight the controversial role, as regards food security, of oil palm cultivation, especially in relation to biofuel production (Meijaard and Sheil 2019), which could increase the risk of competition between land uses and encourage land grabbing (Bassey 2016, Onoja et al 2017). Another study maintains that the increase in land converted for oil palm cultivation in Indonesia could lead to rapid urbanization of the areas surrounding the plantations, which, together with the migration that often accompanies such expansion, could pose a risk to the food security of smallholders and their families (Budidarsono et al 2013). This finding is confirmed by the fact that, according to some publications, indigenous populations are the most heavily affected by oil palm expansion in terms of food security (Manik et al 2013, Mingorría et al 2014, UNICEF 2016), since they are more exposed to changes in their eating habits, switching from traditional high-protein diets (meat and fish) to diets based on less nutritious foods. This is mainly due to the considerable commitment, in terms of time, required for the smallholders to cultivate the oil palm to the detriment of subsistence farming, thereby creating more dependence on the market not only for the sale of palm oil but also for the purchasing of food. These aspects mainly impact women (Julia and White 2012, Elmhirst et al 2017a) and children (UNICEF 2016).

3.3. SDG 3: good health and well-being

From the standpoint of access to social benefits, several studies maintain that oil palm cultivation increases the possibility of access to healthcare for smallholder families, chiefly due to the increased economic means at their disposal thanks to their earnings (Feintrenie et al 2010, Rist et al 2010, Cramb and Curry 2012, Varkkey 2012, Adebo et al 2015, Alwarritzi et al 2015, Potter 2015, Elmhirst et al 2017b, Sibhatu 2019, Qaim et al 2020). In particular, a number of studies (Syahza et al 2011, Gatto et al 2017, Edwards 2019) have found that the widespread cultivation of oil palm has led, indirectly, to the improvement of health facilities in Indonesia, and this is a key element in ensuring more equitable access to the country's national health services (Efendi 2012, Budidarsono et al 2013, Pacheco et al 2017, Grepalma 2020). Analysing a sample of 516 villages throughout Indonesia, 60% of which were totally dedicated to oil palm cultivation, the study found that oil palm-dominated villages perform well on many development indicators, such as schools, roads, incomes, access to electricity and access to health facilities. A survey (Acosta and Curt 2019) conducted in a forested area in Papua (Indonesia) confirmed the major social benefits that oil palm cultivation brings, but also noted the irreversible loss of benefits provided by forests. However, a study by Santika et al (2019) points out that the effects of the palm oil industry on well-being are not always equally distributed among Indonesians and can depend on the site-specific characteristics or on the pre-existing socio-economic situation of the villages prior to the development of oil palm cultivation. In some villages that cultivate oil palm, there is a lower rate of improvement in social and environmental well-being than in villages that do not, irrespective of the location and basic livelihoods of the community. In addition, many communities suffer negative impacts on general well-being due to certain negative factors such as the exploitation of labour and work alienation (Manik et al 2013, Mingorría et al 2014). Attempts are made to overcome the above-described problems by applying sustainability certification standards, reason for which several studies have been dedicated to a comparison of the impacts of various sustainable production approaches on health and well-being (Yaap and Paoli 2014, McInnes 2017). One study in particular (Morgans et al 2018) compared the health impact of RSPO-certified and non-certified plantations in some villages in Indonesian Borneo. Given the fact that health facilities per capita in the areas surrounding the plantations, both certified and non-certified, have been progressively decreasing since 2000, while populations in the villages surrounding the plantations have been growing, one study determined that sustainability certification did not actually increase access to healthcare in relative or absolute terms, but simply slowed down its decline (Morgans et al 2018).

Santika et al (2020) also assessed the impact of RSPO certification on well-being in Indonesian villages by monitoring changes in 18 indicators of socio-economic and socio-ecological well-being. The study shows that the connection between RSPO certification and well-being at village level varies depending on the location and basic nutritional conditions of the village prior to full implementation of the certification principles and criteria. The impacts are positive in villages where the majority of the community was already purchasing staples on the market prior to certification; whereas RSPO certification has been associated with negative results in rural villages oriented towards subsistence farming. Additionally, the same study maintains that improvements in well-being were more evident in locations where plantations had been certified for a longer time, confirming that some benefits of sustainability certification tend to emerge in the long term. Some studies in Indonesia (Lee et al 2020) and Malaysia (Nambiappan et al 2018) show that sustainability certification schemes, such as RSPO and MSPO, contribute in the short term to environmental conservation but have a limited impact on rural development. So further analyses of the long-term impacts of certification on the environment and communities will have to be carried out.

The negative aspects emerging from the analysis of the studies include the impact that the conventional approaches to oil palm production have on the health of the plantation workers (Ahmed et al 2019, Castellanos-Navarrete et al 2019) due—particularly in Indonesia—to the use of hazardous chemicals, to the heavy workloads, occupational accidents and the inadequate healthcare provided by the companies (Moreno-Peñaranda et al 2015). Specifically, female workers are more exposed to serious health risks due to pesticides (Li 2018). Schrier-Uijl et al (2013) also identified an additional environmental—but also human—health risk in the burning of plant biomass to clear land for oil palm cultivation. There are many initiatives in palm oil producing countries that promote the well-being of citizens: one example is in Guatemala where a significant increase in well-being has been achieved through investment in health and food security programmes, medical care in hospitals, medical services on plantations available to workers and to members of the community, community medical programmes, ambulance services, as well as health and nutrition training programmes (Grepalma 2020).

3.4. SDG 4: quality education

Guaranteeing inclusive and equitable quality education and promoting lifelong learning opportunities for all individuals is a key part of the Sustainable Development Agenda, which promotes quality education at all levels (UN 2015). Education is considered an essential factor in improving agricultural production, particularly with a view to sustainability and social equity (Li 2018, Furumo et al 2020). It has, in fact, been demonstrated that a high level of literacy enables a better understanding and subsequent improvement of the agricultural practices related to the production of palm oil, including the implementation of innovations and technologies (Ibitoye et al 2011, Adesiji et al 2016). Two socio-technical analyses of palm oil plantations in Indonesia show that the people working in the production of palm oil tend to be poorly educated or to have an educational background unrelated to the agricultural sector (Alwarritzi et al 2015, Sitepu et al 2020); this condition slows down the transition towards sustainable production (Sitepu et al 2020). The creation of oil palm plantations is often followed by the development of a range of infrastructures such as roads, healthcare structures and, above all, educational facilities (Feintrenie et al 2010, Budidarsono et al 2012, 2013, Obidzinski et al 2012, Schrier-Uijl et al 2013, Pacheco et al 2017, Grepalma 2020, Qaim et al 2020). The majority of the large palm oil companies in Malaysia are involved in building schools to provide education for the children of their workers, thereby generating a positive impact on the standard of living of employees and their families (Dayang Norwana et al 2011). Two major studies (Santika et al 2019, 2020) have also correlated the impact of oil palm plantations with the habits of the villages in procuring staples: from these studies it emerged that where villages were already market-oriented in the procuring of staple foods, access to infrastructure, including education and health, tends to be better than in villages oriented towards obtaining the staples directly. Sustainable palm oil production pays particular attention to educational processes (Lee et al 2020). In particular, Yaap and Paoli (2014) observed that four of the most important standards in the promotion of sustainable palm oil in Indonesia—RSPO, ISPO, ISCC and SAN—require palm oil companies to guarantee access to education for children living in the areas surrounding the plantations. However, one study indicates that, often, such support for improving children's access to education is offered by palm oil companies to the local population to partially compensate for and offset the potential negative consequences that might result from the land-use change that occurs as a result of the creation of the oil palm plantations (Acosta and Curt 2019). The same study points out that the compensation provided to the local population by plantation companies in terms of additional benefits (e.g. education and health) should always be greater than the benefits lost as a result of the planting of the oil palm crops (Acosta and Curt 2019). Another publication highlighted that in Indonesia, due to the development of the palm oil sector, manufacturing companies often provide service access to primary and secondary schools for their employees' children, also facilitating transport, particularly to educational facilities located in remote rural areas (UNICEF 2016). But the same study also points out that sometimes the quality of the education provided is below public standards because teachers are poorly paid and not well trained (UNICEF 2016).

3.5. SDG 5: gender equality

Most studies addressing gender issues connected with the production of palm oil have been conducted in Indonesia and Africa. For example, Li (2015) applied a gender perspective to analyse the impacts of oil palm on men and women from different social groups. The two main models of oil palm cultivation were taken into consideration: large-scale plantations employing both casual and permanent workers, and small-scale plots, both independent and linked to large palm oil companies. Some of the impacts on women included the loss of the land they used for subsistence agriculture (Li 2015, Moreno-Peñaranda et al 2015), greater difficulty in acquiring plots of land for cultivation, labour vulnerability on plantations (Li 2015, Elmhirst et al 2017a, 2017b, Castellanos-Navarrete et al 2019) and the limitation of gender-related employment rights, such as maternity leave and breaks for breastfeeding (UNICEF 2016). Only in the production model with small independent plots do women retain some rights such as taking part in the decision-making of agricultural management, sharing benefits with their husbands and having equal land ownership rights (Li 2018).

In general, male and female workers in oil palm cultivation often have different responsibilities: men are mostly employed for harvesting activities, while women are employed for sporadic tasks, such as weeding or the application of fertilizers, but they are forced to accept more precarious conditions and lower wages than their male counterparts (Li 2015, Elmhirst et al 2017a, 2017b). Some studies (White and White 2012, Li 2015, Elmhirst et al 2017a, 2017b) highlight gender differences even more, underlining that women are generally excluded from taking part in decision-making processes, such as land-transfer agreements or the stipulation of working conditions. White and White (2012) also point out how the advent of palm oil companies has brought about changes in land ownership systems in rural areas in favour of male 'breadwinners', thereby limiting the access of women to land. These constraints also affect women's participation in sharing any benefits generated by oil palm development processes (Ibitoye et al 2011, Bassey 2016, Elmhirst et al 2017a); women generally respond to such obstacles by using alternative strategies that demonstrate their resilience and adaptability to changing circumstances (de Vos and Delabre 2018).

The above-described conditions are confirmed in a study (DTE 2014) conducted in a production area in Papua (Indonesia) that listed various conditions of hardship for women, such as job instability, loss of access to farming land and forest resources, and high food prices. In contrast, another study in Bungo (Indonesia) analysed gender-disaggregated data regarding participation in land-use decision-making and found that the conversion of agroforestry areas into plantations for cash crops, such as rubber and oil palm, was essentially a decision made by men and women together for the purpose of increasing their mutual access to capital (Feintrenie et al 2010, Therville et al 2011).

Other studies, mainly in Africa and South America, maintain that the production of oil palms has had positive effects on gender equality. A study (Adebo et al 2015) conducted in a small province in Nigeria shows that the women involved in the production of palm oil tend to share a number of recurring socio-economic characteristics: they are mainly married, relatively young, have a low literacy level and, first and foremost, they all work on small farms of less than 2 ha in size. The study shows an improvement in the income and standard of living of women involved in the production of palm oil, concluding that efforts to promoting the employment of women in this sector would bring about a reduction in poverty rates among women and their families, especially in rural areas. The same study records positive impacts in terms of gender equality along the entire palm oil production chain, from planting to processing and marketing, as well as among the different types of players involved in the chain such as growers/producers, processors, dealers and consumers; generally speaking, women tend to be more frequently employed in the processing phase of the palm fruit and in marketing activities for the companies, suggesting a diversified level of gender involvement along the production chain (Omonona and Agboje 2013, Adesiji et al 2016, Elmhirst et al 2017a, 2017b). Another study in Ghana (Etuah et al 2020) concludes that involvement in the oil palm activities contributes positively to women's empowerment, but many inequalities in the supply chain still exist between men and women.

A number of initiatives in Guatemala are promoting cross-cutting policies to prevent gender discrimination, fostering the setting up of gender committees to operate as a mechanism for dialogue, protection and support of female workers, for the purpose of safeguarding their rights and advancing their interests within the large companies in the palm oil supply chain (Grepalma 2020).

Gender aspects are taken into account in the production of sustainable palm oil. In particular, multi-stakeholder initiatives (such as RSPO) have been upping their efforts in recent years to safeguard the rights of female workers in the oil palm economy (Elmhirst et al 2017a). A comparative study (McInnes 2017) of the most important existing standards for oil palm sustainability (RSPO, ISCC, ISPO, MSPO, SAN, HCS and RSB) revealed that all standards have criteria that prohibit discrimination, but the definitions of what constitutes discrimination vary widely from one standard to another. With regard to the protection of women, ISCC, RSB, ISPO and MSPO do not contain specific criteria (McInnes 2017), while RSPO and HCS promote a productive gender-sensitive approach, for example by including criteria and mechanisms to protect women from sexual harassment in the workplace (Yaap and Paoli 2014, McInnes 2017, Elmhirst et al 2017a) and by developing, in the case of RSPO, practical guidance on gender inclusion and compliance, approved in 2021 to integrate the 2018 RSPO principles and criteria and the 2019 ISH standard.

3.6. SDG 6: clean water and sanitation

The expansion of oil palms has led to the conversion of forests in recent decades, with damaging effects on ecosystem services, loss of biodiversity and reduced water quality (Pacheco et al 2017, Elmhirst et al 2017a). Many studies report negative impacts in Southeast Asia (particularly, in Indonesia) where conventional oil palm cultivation is acknowledged to be the major cause of water pollution (Muyibi et al 2008). Large amounts of fertilizers are used in conventional oil palm cultivation in Indonesia (FAO 2005), and palm oil mill effluent (POME) is also a water-polluting discharge (Wu et al 2010, Moreno-Peñaranda et al 2015) with the power to degrade aquatic ecosystems (Comte et al 2015, de Jong et al 2015, Moreno-Peñaranda et al 2015). Soil erosion can also be caused by oil palm cultivation, especially when the palm canopies in the plantations have not yet reached full development (Lee et al 2012). In these cases, eroded soil can enter water bodies, further degrading the quality of the water (Cramb and Curry 2012, Obidzinski et al 2012).

The expansion of oil palm cultivation also risks competing with local agriculture by reducing the availability of arable land and water for the subsistence farming that is crucial to some indigenous peoples (Oosterveer 2014). One example of this is the expansion of oil palm plantations in the region of Tripa (Indonesia), which has led to water shortages for the rice fields (Tata et al 2010). Further studies conducted in various areas of Indonesia show an association between oil palm expansion and the negative impacts on water availability and quality, with direct consequences on the availability of drinking water for the local populations (Li 2015, 2018, Moreno-Peñaranda et al 2015); leading, in turn, to consequences for public health (Rist et al 2010, Dradjat 2012, Manik et al 2013, Moreno-Peñaranda et al 2015).

In this regard, a UNICEF report (UNICEF 2016) describes a negative impact on water quality caused by palm oil plantations in Indonesia as a result of the leaching of pesticides and agrochemicals, the discharge of POME and hydrocarbon contamination in rivers. This has led to reduced access by local communities to important sources of drinking water, with negative consequences on health, particularly that of children. The study underlines the need to undertake sustainable development in the palm oil sector with a view to achieving the 2030 SDGs. A study conducted in West Kalimantan (Indonesia) on the impacts of oil palm expansion showed lower water availability in a business-as-usual scenario compared to a sustainable intensification scenario, where the plantations had only been placed in areas suitable for expansion. Sustainable production provides more ecosystem services than the business-as-usual scenario without significantly affecting palm oil crop yields, but the quality of the habitat suffers degradation in both scenarios (Sharma et al 2019). Additionally, the implementation of integrated management practices in oil palm plantations, including the use of water harvesting and storage technologies and protection by means of riparian buffer zones (Luke et al 2019), is reported to be key to achieving sustainability in the oil palm industry (Nambiappan et al 2018, Foong et al 2019). The leading internationally recognized sustainable production standards (RSPO, ISCC, SAN and ISPO) include criteria for water rights and the shared use of water resources (Yaap and Paoli 2014). In particular, the RSPO certification standard lays down, in this sense, a number of principles aimed at reducing water pollution and specific criteria in order to identify and monitor objectives and targets to reduce impacts and improve water quality (Lord and Clay 2006, Furumo et al 2020, Lee et al 2020, Santika et al 2020).

3.7. SDG 8: decent work and economic growth

SDG 8 is the most widely discussed in the studies analysed, with 59 papers out of 82 addressing these aspects. Considering the relevance and the complexity of the topics under this SDG, this section is structured by differentiating the impacts of palm oil on the two sub-items of this SDG.

3.7.1. Decent work

The palm oil sector has created important employment and income opportunities in rural areas in many countries, compensating for the slow absorption of labour in urban areas. Workers on medium-sized and large farms are classified into permanent, seasonal or casual categories depending on the tasks performed (e.g. sowing, weeding, fertilizer application, harvesting, and channel cleaning), while small farmers are classified according to origin, with differences between immigrants and natives. As a rule, the conditions of permanent workers on large-scale plantations are better than those of permanent workers on medium-sized plantations. Additionally, the wages of permanent plantation workers tend to be higher and more regular than the economic income of small farmers (Pacheco et al 2017). Wages are higher if plantations have sustainability certification, according to a study in Colombia (Furumo et al 2020). The drawback of sustainable production certifications is the cost of obtaining them, which is often out of reach for small landowners, thereby rendering sustainability certification financially accessible exclusively for large plantations operating in a primarily profit-oriented monoculture farming regime (Azhar et al 2017).

Some studies, however, highlight the negative aspects of employment in the palm oil supply chain. The problems reported are varied and are mainly related, on large plantations, to: low workers' wages (Majid Cooke 2012, Manik et al 2013, Sinaga 2013, Kaur 2014, Li 2015, Bassey 2016, Castellanos-Navarrete et al 2019, Pye 2019, Santika et al 2020); the precarious and casual employment formulas used to lower labour costs (Manik et al 2013, Li 2015, 2018); the low taxes paid by the companies that fail to compensate for costs related to local development (Santika et al 2019); and, the working conditions of women who are often forced into poorly paid, casual and even dangerous jobs (Elmhirst et al 2017a, Li 2018). The denial of workers' basic rights (Manik et al 2013, Sinaga 2013, Kaur 2014, Pye 2019) and smallholders' difficulties in accessing land (Castellanos-Navarrete et al 2019). Moreover, oil palm development has generated both internal migrations, from the most populated to rural areas, mainly due to the demand for seasonal workers (Pye et al 2012), and international migrations, such as that from Indonesia to Malaysian plantations to compensate for labour shortages in Malaysia (Tirtosudarmo 2009). These migrations have generated further negative aspects such as the phenomenon of workers migrating towards areas with plantations without their respective families in tow, a situation that potentially results in the fragmentation of families (Kaur 2014, Li 2018), and the migration of often illegal workers from other nations (Majid Cooke 2012, Kamalrudin and Abdullah 2014, Kaur 2014, Ludin et al 2014, Pye 2019).

In order to limit these negative effects, it is important for all stakeholders involved in the production chain, together with politicians, investors and civil society, to agree on the need for responsible palm oil production that avoids the conversion of natural ecosystems, maximizes ecosystem services, respects Earth and, above all, guarantees the fair redistribution of socio-economic benefits (Persey et al 2011, Schrier-Uijl et al 2013, Elmhirst et al 2017a, Edwards 2018, Sitepu et al 2020). For example, according to a number of studies conducted in Indonesia, smallholders' implementation of a sustainable approach to oil palm cultivation through the adoption of standard certification schemes such as ISPO and RSPO leads not only to greater social benefits than conventional production, but also to better economic outcomes (Morgans et al 2018, Adiprasetyo et al 2019). It is important to point out that the criteria contained in sustainable production certification schemes do not only address compliance with employment and migration standards, but also refer to other services, such as training, housing, water supply, electricity, insurance (Dayang Norwana et al 2011) and other basic social services such as healthcare and education (Obidzinski et al 2012). In particular, in 2019, RSPO published the first industry guide entitled 'Decent Living Wage Guidance' for oil palm workers, for the purpose of evaluating the adequacy of the wages paid to ensure decent living conditions for workers and their families.

3.7.2. Economic growth

The contribution of palm oil to economic growth, especially in rural areas, has increased considerably over the years (McCarthy and Cramb 2009, Budidarsono et al 2013, Azhar et al 2017, Pacheco et al 2017, Sharma et al 2019). The most prominent data concern the substantial contribution to economic growth that palm oil development has made to producer countries, providing employment and increasing incomes for all players throughout the production chain (Susila 2004, Dayang Norwana et al 2011, Hoyle and Levang 2012, Ohimain et al 2014, Moreno-Peñaranda et al 2015, Potter 2015, Adesiji et al 2016, Elmhirst et al 2017a, Edwards 2018, Muhammad et al 2019, Purnomo et al 2020, Qaim et al 2020, Sitepu et al 2020). Some studies maintain that the economic and occupational growth associated with the development of the oil palm industry can also be maintained through the implementation of sustainable practices that not only provide revenues for national governments, companies and small farmers, but also the environmental protections required (Yaap and Paoli 2014, Pirker et al 2016, Purnomo et al 2018, 2020, Grepalma 2020).

Over the years, the expansion of the oil palm sector has become a controversial issue, which has not only had several negative social and environmental impacts (Foong et al 2019), but also benefits related to the generation of tax gains for the producer countries (Dradjat 2012, Otieno et al 2016, Pacheco et al 2017, Nambiappan et al 2018) and revenues for the many large and small landowners involved in the production chains (Feintrenie et al 2010, Rist et al 2010, Dradjat 2012, Silalertruksa et al 2012, Budidarsono et al 2013, Ofosu-Budu and Sarpong 2013, Mingorría et al 2014, Alam et al 2015, Alwarritzi et al 2015, Pacheco et al 2017, Elmhirst et al 2017b, Dib et al 2018, Papilo et al 2018, Acosta and Curt 2019, Balde et al 2019).

Considering the different geographical areas of production analysed in the existing studies, it emerges that the production of palm oil is much more limited in Africa than it is in Southeast Asian countries, mainly featuring as a traditional agroforestry system to enable small farmers to diversify their production (Potter 2015). In Africa, palm oil processing is mainly carried out using local artisanal systems, such as traditional mills, that generate employment opportunities and help diversify income (Ayodele 2010, Nkongho et al 2014, Pacheco et al 2017, Qaim et al 2020). Alongside this artisanal production, there are also some medium- and large-scale schemes that supply domestic markets without meeting the full demand, which is offset by importing palm oil from the more economically competitive markets of Malaysia and Indonesia. In these two countries, the sector expanded between the 1960s and 1970s (Ibitoye et al 2011), aided by public sector policies and institutional and private structures that facilitated investment along the entire production chain (Pacheco et al 2017). On the South American continent, the palm oil production sector only began to develop in the early 2000s, with the only exception of Colombia where it started in the 1990s (Rueda-Zárate and Pacheco 2015).

The expansion of oil palm cultivation globally has undoubtedly accelerated deforestation problems, especially in Malaysia and Indonesia (Pacheco et al 2017), but it has also contributed to the economic growth of national governments, leading to increased incomes and higher employment levels locally, and spillover effects in terms of the development of services and infrastructure in production areas (Shimizu and Desrochers 2012, Pacheco et al 2017, Dib et al 2018). Although the expansion of oil palm cultivation has become a profitable option for many smallholders (Obire and Putheti 2010), this crop is often only available to farmers who can afford the initial capital outlay to develop new plantations; farmers in indigenous communities have often had so little capital available (Rist et al 2010) that many have been forced to give up their land, selling it to larger landowners in order to cope with increased food prices and the rising cost of living (Pacheco et al 2017).

The development of oil palm plantations with related fruit processing facilities generates positive impacts on local realities by speeding up the development of infrastructure development (road building, health and education facilities) and stimulating the economy. The development of cash crops such as palm oil has also prompted a transition from subsistence farming to market-oriented production, and this change has generated increased employment opportunities (Budidarsono et al 2013). It is also interesting to note the findings of a study conducted in the province of Riau, Sumatra (Indonesia) that observed an increase in wealth and investment in the non-agriculture sector in some villages engaged in oil palm cultivation (Budidarsono et al 2013, Löffler et al 2014).

In a comparison of farming systems, it was found that smallholders growing oil palm under a monoculture regime tend to earn more than those who combine traditional and cash crops through diversified agriculture, and this is driving the transition from traditional agroforestry systems to monoculture oil palm plantations (Feintrenie et al 2010).

3.8. SDG 10: reduced inequalities

The existence of inequalities in the palm oil production sector may be due to different causes and groups of people. The main elements of inequality concern men vs. women, smallholders vs. large-scale producers and indigenous populations vs. large-scale producers. A study conducted in the province of Riau (Indonesia) also reports on the existence of economic inequalities between rural and urban areas (Syahza et al 2011). It maintains that in order to reduce these inequalities all the players in the oil palm supply chain should be involved, from local communities to economic operators and local governments, in order to convince the local populations of the potentially positive effects of the sustainable development of oil palm plantations, i.e. potential increases in income and consequent increases in purchasing power, effects with the power to improve the entire welfare system of rural areas.

According to Li (2018), sustainable development cannot be achieved unless everyone has the resources needed to achieve well-being; it cannot, therefore, be achieved without social equity. All too often the cost–benefit ratio connected with oil palm expansion differs on the basis of social class, community of origin, age and gender (Dayang Norwana et al 2011, Jelsma et al 2017, Elmhirst et al 2017a, Li 2018, Castellanos-Navarrete et al 2019), which is why there is an urgent need for an institutional framework to assist smallholders and improve the distribution of benefits in the sector (Elmhirst et al 2017a, Li 2018, Grepalma 2020, Qaim et al 2020). According to a study by Acosta and Curt (2019), investors and the Indonesian government share about 80% of the benefits generated by oil palm plantations, while only 14% of the benefits (infrastructure, employment, education and health) go to local populations. Another study shows that the expansion of oil palm cultivation in Indonesia has brought about improvements in the standard of living of smallholders in certain areas but that it has also generated economic and social costs (Santika et al 2019) due to increasing inequalities in the distribution of benefits which, in most cases, are only shared between rich farmers and skilled migrants, thereby giving rise to social inequalities and marginalization (Obidzinski et al 2012, Oosterveer 2014, Muhammad et al 2019).

Furthermore, large-scale producers have often expanded their plantations without carrying out the required prior consultations with the local populations (Sheil et al 2009, Feintrenie et al 2010, Rist et al 2010, Nkongho et al 2014), generating conflict with indigenous communities (Cramb and Curry 2012, Hoyle and Levang 2012, Oosterveer 2014, Abram et al 2017, Pacheco et al 2017). In Malaysia and Indonesia, the expansion of oil palm plantations into more remote areas has also led to indigenous peoples being displaced from their native lands (Alam et al 2015, Hidayat et al 2018). A World Bank report (Persey et al 2011) points out that conflicts between indigenous communities and companies have often arisen due to ambiguities in the rights governing the use of resources and land (Dradjat 2012, Mingorría et al 2014, Elmhirst et al 2017b, Hidayat et al 2018, Qaim et al 2020). Furthermore, Onoja et al (2017) underline the existence of a dangerous trend of land grabbing for oil palm expansion across Africa (Nkongho et al 2014, Bassey 2016). This is why sustainability certification schemes focus special attention on the need to involve local communities in decision-making processes. RSPO, for example, includes a mandatory requirement to obtain free prior informed consent from local communities before commencing any kind of project (Yaap and Paoli 2014). Another inequality is generated by the fact that farmers do not all have the same possibility to access capital and land, with those having availability of land and capital benefitting more from oil palm cultivation than those who are hampered by constraints and limitations in this sense (Krishna et al 2017, Dib et al 2018). Lack of access to capital can often oblige smallholders to sell their land (McCarthy 2010, Manik et al 2013, Dib et al 2018). Santika et al (2019, 2020) also demonstrate that the socio-economic impacts of oil palm expansion differ depending on the site-specific characteristics of the villages and, in particular, the basic socio-economic conditions of the villages prior to oil palm expansion. According to some studies, the adoption of practices for the sustainable production of palm oil brings about greater economic, environmental and social benefits than conventional production, benefits that are perceived by the farmers themselves (Elmhirst et al 2017a, Adiprasetyo et al 2019). Another study (Yaap and Paoli 2014) that analyses four certification standards—RSPO, ISCC, ISPO and SAN—shows that all four contain rules and principles aimed at preventing any form of discrimination related to race, gender, social class, sexual orientation, disability or political affiliation.

4. Synoptic overview

The analysis clearly shows the close connections between the various SDGs. For example, the significant contribution of palm oil production to poverty reduction (SDG 1) is closely interlinked with the achievement of other goals such as economic growth (SDG 8), better health and well-being (SDG 3), reduced malnutrition (SDG 2) and quality education (SDG 4); although this does not always correspond to the achievement of other goals such as decent work (SDG 8), gender equality (SDG 5) and reduced inequalities (SDG 10). A major result of this analysis is the clear link between palm oil production and the socio-economic development of local communities, where a direct contribution to poverty reduction and economic growth has been observed with a consequent increase of food security in terms of physical, social and economic access to sufficient, safe and nutritious food, especially in rural areas (Susila 2004, Obire and Putheti 2010, Schrier-Uijl et al 2013, Kamalrudin and Abdullah 2014, Edwards 2018, Ahmed et al 2019) and with higher benefits for small producers who grow oil palm in association with other crops (Feintrenie et al 2010, Fu et al 2010, Kremen et al 2012, Azhar et al 2017). In fact, independent farmers who succeed in combining oil palms with other crops such as rice or fresh vegetables have more chances to guarantee food security and alleviate malnutrition with access to a varied diet and different types of food (Ayodele 2010, Fu et al 2010, Budidarsono et al 2012, Kremen et al 2012, Li 2015, 2018, Azhar et al 2017, Khatun et al 2017, Grepalma 2020).

It was also found that the achievement of some of the SDGs is often facilitated by the implementation of sustainable palm oil production practices. This particularly applies to increased quality education (SDG 4), better health and well-being (SDG 3), and access to clean water and sanitation (SDG 6), which are often referred to as co-benefits of the sustainable cultivation of oil palm plantations.

However, many elements of social inequality exacerbated by the expansion of oil palm plantations emerge from this analysis, mainly in relation to conflict arising over access to land and ownership issues between the local communities and the companies managing the vast plantation areas (Sheil et al 2009, Feintrenie et al 2010, McCarthy 2010, Rist et al 2010, Cramb and Curry 2012, Hoyle and Levang 2012, Manik et al 2013, Nkongho et al 2014, Oosterveer 2014, Abram et al 2017, Krishna et al 2017, Pacheco et al 2017, Dib et al 2018). Furthermore, from this analysis it emerges that the economic growth generated by palm oil production is not always accompanied by decent working conditions with too low workers' wages in some cases (Majid Cooke 2012, Manik et al 2013, Sinaga 2013, Kaur 2014, Li 2015, Bassey 2016, Castellanos-Navarrete et al 2019, Pye 2019, Santika et al 2020), precarious and casual employment formulas used to lower labour costs (Manik et al 2013, Li 2015, 2018), low taxes paid by the companies that fail to compensate for costs related to local development (Santika et al 2019), and worst working conditions for women who are often forced into poorly paid, casual and even dangerous jobs (Elmhirst et al 2017a, Li 2018).

Figure 1 shows a graphical representation of a selection of the 82 studies analysed, reporting only those that mention a markedly positive or markedly negative impact for each SDG (the total number of studies for each SDG as well as the number of the selected studies reporting markedly positive (P) or negative (N) effect are reported in brackets in the figure), distributed by the year of publication. According to the aim of this analysis to identify positive and/or negative contributions of palm oil to the socio-economic SDGs, the studies reporting neutral positions were intentionally not included in the graph as they would complicate the graphical visualization without adding useful evidence to evaluate the general positive or negative results for each SDG.

Figure 1. Refer to the following caption and surrounding text.

Figure 1. Distribution of studies according to year of publication and impact for each SDG: positive (above the line) or negative (below the line). For each SDG, the total number of studies as well as the selected number of studies reporting markedly positive (P) or markedly negative (N) effect are reported in brackets. Spheres of the same color refer to the same SDG. The size of the sphere is proportional to the number of studies. Distribution along the x-axis indicates the year of publication of the studies analysed. Positioning along the y-axis is merely an expedient to minimize the overlapping of the spheres and does not indicate a greater or lesser positive or negative impact.

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What clearly emerges from the graph in figure 1 is that, for some SDGs, the spheres are larger (e.g. SDG 1, SDG 2, SDG 3, SDG 8 and SDG 10), indicating that the number of studies addressing those specific topics is greater than for other SDGs to which less attention in the literature is paid. Furthermore, in general, the larger spheres are above the line, showing a preponderance of studies indicating markedly positive impacts compared to the number of studies reporting markedly negative impacts, with a trend that seems to have increased particularly over recent years, culminating in 2019. The increased number of studies reporting positive effects recorded in recent years could conceivably be related to the increased volume of certified sustainable palm oil, which according to RSPO data (RSPO 2021) today accounts for 19% of total production. Consequently, the greater number of positive impacts on socio-economic indicators reported by the most recent studies may be due to sustainable production, reflecting what clearly emerges from the general analysis of the studies that the implementation of sustainable palm oil production schemes makes it possible to improve many indicators of the socio-economic impact related to the expansion of oil palm cultivation (Santika et al 2019).

Considering that the aim of this analysis is to provide an overview of the positive and/or negative impacts described in the literature for the socio-economic aspects related to palm oil, it appears quite clear that, in general, palm oil production has positive implications for poverty reduction (SDG 1), zero hunger (SDG 2), good health and well-being (SDG 3), quality education (SDG 4), and decent work and economic growth (SDG 8), whose spheres are in general larger above the line (figure 1). Conversely, palm oil production seems to negatively affect other SDGs, such as gender equality (SDG 5), clean water and sanitation (SDG 6), and reduced inequalities (SDG 10), with larger spheres mainly below the line. A particular trend is observed for studies addressing SDG 8, which is composed of two different sub-topics related to decent work and to economic growth, often differently affected by palm oil production. In general, it has been observed that the studies which report positive implications refer mostly to the economic growth ensured by palm oil production while those studies that report negative impacts refer mostly to poor work conditions in palm oil plantations.

5. Conclusion

It is difficult to draw final conclusions and uniform views from the review of the existing literature. The mass of analysed documents provides different, sometimes even contradictory perspectives, highlighting the nuances and varied facets of the contribution of palm oil to the eight SDGs, some of which are inevitably interconnected. These considerations are also confirmed by a very recent study published by Ayompe et al (2020). In general, the majority of the studies analysed concurs with the fact that palm oil cultivation plays a crucial role in boosting the economy and livelihoods of the local communities in many developing producer countries. What emerges from the analysis of the publications is that the production of palm oil makes a significant contribution to reducing poverty by increasing food security, i.e. the physical, social and economic access to sufficient, safe and nutritious food to meet the needs of individuals and communities. Some of the documents analysed, however, maintain that the expansion of oil palm plantations has, in some cases, exacerbated social inequalities; chiefly due to conflicts arising over access to land and ownership issues between local communities and the companies managing the vast plantation areas. Furthermore, according to the existing literature, the economic growth generated by the palm oil production chain is not always accompanied by decent working conditions: the work tends to be heavy and strenuous, harmful chemicals are used, workers are not protected, and the wages are poor. It is, however, important to point out that many of the evaluations made in this analysis should be considered within the context of the countries where the studies were conducted, given the fact that many of the more negative aspects reported exist in general, independently of the palm oil sector, being linked to traditional, cultural, political and socio-economic circumstances. In fact, as highlighted by Santika et al (2019, 2020), many of the implications of palm oil production on the general well-being of local communities often differ depending on the site-specific characteristics of the villages, the initial socio-economic situation and the different livelihood systems of the communities.

In general, a major aspect emerging from the analysis is that the achievement of some SDGs is often facilitated by the implementation of sustainable palm oil production practices. This particularly applies to increased quality education (SDG 4), better health and well-being (SDG 3), and access to clean water and sanitation (SDG 6), which are often referred to as co-benefits of the sustainable cultivation of oil palm plantations. Thus, we can conclude that the application of sustainability certification schemes plays a key role in improving the socio-economic and environmental performances of palm oil production. As highlighted by Meijaard and Sheil (2019) and Yap et al (2021), the certification of sustainable palm oil production, if credible, accessible and applied with a transparent approach, can reduce environmental pressure, increase employment and improve economic livelihoods for the people living in the production areas in terms of working conditions, infrastructure, services and higher wages, with a consequent reduction of poverty rates, an increase in quality education, as well as better access to food and healthcare systems.

Data availability statement

No new data were created or analysed in this study.

10.1088/1748-9326/ac6e77
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