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Agrofuels: key driver in new landgrabbing wave
DTE 93-94, December 2012
Agrofuels are often promoted by the agrofuels industry, investors and government officials as a means of providing livelihoods for rural communities, but how does this square with the fact that agrofuels are part of the landgrabbing problem in countries like Indonesia?
The pro-agrofuel argument is that crops grown for fuels can help mitigate climate change by reducing carbon emissions because they can be used instead of fossil fuels for energy and transport. They can also fight poverty, according to these arguments, by providing livelihoods for farming communities.
In reality, however, agrofuels are taking a heavy toll on people and environment. Frequently, the impacts on small scale farmers, local communities and the environment are devastating. Many agrofuels are also bad for the climate because carbon-rich forests and peatlands are (directly or indirectly) cleared to grow them.[1] However, as with many policy developments which pitch business and political interests against the environmental and social interests of the poor, these impacts are often inaccurately measured or conveniently overlooked.
EU-RED boosting the palm oil boom
The long-lived palm oil ‘boom’[2] has been the staple in Indonesia’s national income for over three decades. In 2008, oil palm exports/sales/income represented 2.8% of the country’s GDP.[3] Since Indonesia’s economic collapse in 1997-98, palm oil has been a key commodity asset in President Susilo Bambang Yudhoyono’s push to increase foreign investment. Exports of crude palm oil, refined palm oil and palm kernel oil have increased from US$ 8.7 billion in 2007 to $20.4 billion in 2011. India, China and Malaysia are the top destination countries for palm oil exports.[4]
More recently, the palm oil boom has been boosted by market expansion of agrofuels resulting from the European Union’s Renewable Energy Directive (RED)[5] The RED requires each EU Member State to ensure that 10% of their transport fuel consumption is generated from renewable energy sources by 2020.[6] The prospect of a long-term lucrative European market for agrofuels has generated investor confidence in palm oil and a strong incentive for commercial investment in land acquisition for agrofuel plantation development.[7] Producing palm oil for the global commodity markets continues to be an attractive economic-development pathway for Indonesia[8] and government targets have now been set to increase palm oil production by 15 million tonnes by 2020, from 25 million tonnes in 2012 to 40 million tonnes.[9]
Agrofuels: key driver
Market opportunities for bioenergy production are inflating a “new bubble” of speculative investments or landgrabs.[10] The EU’s thirst for biodiesel from palm oil to fulfil EU RED targets for renewable energy threaten to drive yet more land acquisitions in Indonesia. Over three quarters of the EU’s agrofuels consumption will be met by biodiesel,[11] 20 per cent of which is projected to originate from palm oil produced in Indonesia and Malaysia.[12] In parallel, agrofuels continue to feature prominently in Indonesian government development plans,[13] with a predicted increase in biodiesel production from 1.8 billion litres in 2012 to 2.2 billion litres in 2013 and a conservative projected increase in exports to 1.5 billion litres in 2013.[14]
Translated into land figures, over 60 million hectares– an area nearly five times the size of England – could be converted to palm oil (for both fuel and non-fuel use) and agrofuel production by 2030.[15] According to the International Land Council (2011), 60 percent of grabbed lands are devoted to biofuels.[16]
As Santurino et al (2012) state, “There is no consensus as to how much land has been changing hands and on the methodologies of identifying, counting and quantifying land grabs” This is particularly the case when trying to assess the more complex impacts of landgrabbing in Indonesia resulting directly from EU demand for palm oil for biodiesel. This is largely because palm-oil is a ‘flex-crop’ with multiple markets and uses, making it difficult to separate out whether crops like palm oil are being grown for fuel or non-fuel markets at any one time.[17]
However, there is a consensus that landgrabbing is underway and that it is significant (White et al. 2012)[18] and it is evident that Europe’s reliance on biodiesel to fulfil renewable energy targets could have significant land-use implications. Indeed, recent evidence suggests that globally, two thirds of big land deals in the past ten years are to grow crops that can be used for biofuels, such as palm oil and jatropha. [19]
The challenges of linking agrofuels to land grabs “One implication of the flex crop/commodity phenomenon is the complexity in understanding land grabbing .”(i) Identifying the direct land-grab impacts of agrofuels resulting from the EU RED is complex for several reasons: palm oil is a 'flex-crop', i.e. a crop which has multiple uses which can be flexibly interchanged. Palm oil has prominent uses as a food, biodiesel and also has commercial/industrial uses. Hence, land grabbing for palm oil is influenced by multiple factors (food, energy/fuel and policy pressures/climate change mitigation strategies) which, “are articulated through increasingly entangled global commodity value chains, making it impossible to reduce all these heterogeneous dynamics to a single driver of land grabbing ”.(ii)
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The “Jatropha hype” Jatropha, an oil-seed-producing shrub from Central America has recently been favoured as a potential alternative feedstock in the production of biodiesel. One of jatropha’s key qualities is its capacity to grow on marginal land (see separate article). Those in the business community, and government, who support the expansion of first generation biofuels, have been actively promoting jatropha as potential solution to the ‘food not fuel’ conflict surrounding agrofuels production. However, many of the positive attributes of jatropha, including claims of high yields with low inputs, drought tolerance and pest and disease resistance, have not been scientifically verified.[20] As is the case for most agrofuel feedstocks, assessments of the social and environmental impacts of jatropha are often inadequate because they are based on projections from extrapolations and estimates rather than neutral, independent scientific research, observations and empirical evidence. They do not sufficiently consider key agronomic and ecological factors of the jatropha’s performance as an industrial-scale crop. Small-scale trial plantings do not provide a realistic context in which to assess Jatropha performance as an industrial-scale crop. When planted on a large-scale as a monoculture crop (or as part of an inter-cropping system), Jatropha competes with other crops for natural resources such as radiation (heat and light from the sun), water and nutrients and thus behaves differently than in small scale plantings. But no long-term, detailed, realistic agronomic studies have been carried out on the yield and resource efficiency of jatropha at the industrial scale or within a business model. Avoiding the ‘inconvenient truths’ There has been a repeated tendency to avoid ‘inconvenient truths’ within the agrofuels sector, ignoring data which identifies negative social and environmental impacts and focusing on data which supports business and political interests. To date, hundreds of millions of dollars of public and private funds may well have been invested in jatropha crop trials and research – money which could have otherwise been invested in more viable energy solutions. Yet jatropha is showing a significant shortfall on the fundamental requirement of yield. It is likely to take years of selective breeding or modification to remedy that, and many more millions of dollars. Have governments across the world learnt anything from the mistakes made by heavily investing political, commercial and financial capital in damaging first generation biofuels? If so, jatropha must be allowed onto the agrofuels market only if it can pass stringent environmental, social and economic tests. If it fails, the claims about jatropha’s potential as a champion agrofuel feedstock will indeed, be exposed as commercial hype. This text is based on information in: Peter Baker & Zoheir Ebrahim, Jatropha – An Update Part 5: A systemic knowledge failure, CABI UK, 2012 |
‘Virtual’ landgrabbing - profiteering from ‘vacant’ land
Oil palm has a history of delivering a high rate of return, making it an attractive and reliable investment product. The 2020 deadline for the EU RED renewable energy targets has sparked a commercial scramble to grab vast swathes of land, quickly. This often results in failure to gain the consent of local communities whose livelihoods, local biodiversity and social and cultural wellbeing are dependent on the land. This situation is further exacerbated by the lack of Indonesian State policies and enforceable EU RED social sustainability criteria to ensure that local communities’ land rights are recognised and their right to give or withhold their free prior and informed consent (FPIC) to projects targeting their areas are respected.
Landgrabbing is also a highly speculative exercise which can reap significant rewards for the savvy entrepreneur. For those who lack the capital to implement a designated project or who see the potential to ‘buy now, develop later’, acquiring land for oil palm development can be a prosperous business. This approach to land acquisitions has been termed ‘virtual-land grabbing’.[21]
What McCarthy et al term ‘virtual land-grabs’ feature a “gap between plans as stated and schemes as implemented”. Companies may claim they are acquiring land for agrofuel production, and say they are contributing to global efforts to solve the climate and energy crisis. In reality, large areas of land is acquired and immediately cleared then left vacant as a capital investment for future development or profitable sale. These acquisitions are a strategy of investment risk mitigation which allows companies to pursue their own interest by securing the area for future expansion, generating up-front capital (largely through selling off the timber) and offsetting plantations investment costs.[22] Some estimates show that European firms have already claimed over five million hectares of land for agrofuel development across the global South.[23]
According to John McCarthy (2012), “virtual land acquisitions associated with oil palm are now very extensive: by 2010, 26 million ha of oil palm plantation licenses had been issued, despite a capacity only to plant around 500,000 ha of oil palm each year”.[24] State authorities have the provisions to remove concessions when land remains unproductive for long periods of time, but commonly fail to use them .[25] Consequently, millions of hectares of forested or marginal land[26] which is otherwise essential as a carbon store, for biodiversity and natural resources conservation or as agricultural land for food crops, lay to waste, in some cases for up to a decade or more. [27]
palm oil landgrabs in Kalimantan, Sumatra and Papua CIFOR research shows that to date most plantation concessions have been given out in Kalimantan and Sumatra. By 2011, nearly 11 million ha of land had been allocated for oil palm estates on these islands (see Table). On average, less than half of this area has actually been developed into productive plantations. Despite this, new applications for oil palm plantation concessions are still being encouraged with the main target for these being in eastern Indonesia, particularly Papua, where the area of land acquired for commercial plantations has increased significantly. Oil palm is by far the dominant plantation commodity for which land is being acquired. In 2010, according to CIFOR, 142,000 ha of land were allocated for oil palm plantations in Papua, of which 38 000 ha have been developed into productive plantations. About 1.5 million ha of new plantation permits are being processed by government authorities, according to the Papua Province Plantations Bureau, while an additional 2.1 million ha of oil palm plantations and 0.4 million ha of sugarcane estates are at the proposal stage.[28] |
Binding sustainability criteria
In terms of winners and losers in the agrofuels boom, it is clear that commercial interests come out on top. As long as food crops, such as palm oil, are legitimised for energy generation, land availability for food production and rural livelihoods will be undermined.
The EU RED was established when the impacts of first generation agrofuels on people and the environment were poorly researched, understood or anticipated. As a result, it is fuelling the transformation of land into a global commodity – at the expense of climate, environment and people. The European Commission has a responsibility to correct policy mistakes by introducing binding social sustainability criteria for agrofuel production and taking strong action towards removing first generation agrofuels from the EU’s renewable energy targets.
[2] Casson, A. 2000. The hesitant boom: Indonesia’s oil palm sub-sector in an era of economic crisis and political change. Occasional Paper No. 29. Center for International Forestry Research, Bogor, Indonesia.
[3] Rizaldi Boer, Dodik Ridho Nurrochmat, M. Ardiansyah, Hariyadi, Handian Purwawangsa, and Gito Ginting Reducing agricultural expansion into forests in Central Kalimantan Indonesia:Analysis of implementation and financing gaps Center for Climate Risk & Opportunity Management Bogor Agricultural University 2012
[4] Indonesian Ministry of Trade statistics at http://www.kemendag.go.id/en/economic-profile/indonesia-export-import/export-growth-hs-6-digits, and http://www.kemendag.go.id/en/economic-profile/10-main-and-potential-commodities/10-main-commodities.
[5] The Global Land Grab: A Primer. Transnational Institute Agrarian Justice Programme, October 2012. Available from: http://www.tni.org/sites/www.tni.org/files/download/landgrabbingprimer_0.pdf
[6] Article 3, (4). Renewable Energy Directive. See DTE’s agrofuels updates for more details on the RED and EU policy.
[7] The Global Land Grab: A Primer. Transnational Institute Agrarian Justice Porgramme, October 2012. Available from: http://www.tni.org/sites/www.tni.org/files/download/landgrabbingprimer_0.pdf
[8] Stockholm Environment Institute. Studies reveal palm oil impacts in Southeast Asia, propose EU policy changes. 16 October 2012. Available from: http://www.sei-international.org/-news-archive/2491?format=pdf
[9] Rizaldi Boer, Dodik Ridho Nurrochmat, M. Ardiansyah, Hariyadi, Handian Purwawangsa, and Gito Ginting Reducing agricultural expansion into forests in Central Kalimantan Indonesia:Analysis of implementation and financing gaps Center for Climate Risk & Opportunity Management Bogor Agricultural University 2012
[10] De Schutter, O. 2011. How not to think of land-grabbing: three critiques of large-scale investments in farmland. Journal of Peasant Studies, 38(2), 249–79.
[11] Stockholm Environment Institute. Studies reveal palm oil impacts in Southeast Asia, propose EU policy changes. 16 October 2012. Available from: http://www.sei-international.org/-news-archive/2491?format=pdf
[12] Holt-Gime´nez, E. 2007. Biofuels: myths of the agro-fuels transition. Food First Backgrounder, 13(2). Available from: http://www.foodfirst.org/node/1711 [Accessed 19 February 2009].
[13] Caroko, W., Komarudin, H., Obidzinski, K. and Gunarso, P. 2011 Policy and institutional frameworks for the development of palm oil–based biodiesel in Indonesia. Working Paper 62. CIFOR, Bogor, Indonesia Available from: http://www.cifor.org/publications/pdf_files/WPapers/WP62Komarudin.pdf.
[14] USDA Foreign Agricultural Service (GRAIN), Indonesian Biofuels Annual 2012, Report No. ID1222.Approved by:Prepared By: Ali Abdi. Prepared by: Jonn P Slette/Ibnu E Wiyono
[15] Vidal, John. The Guardian, Tuesday 23 November 2010. Indonesia eyeing $1bn climate aid to cut down forests, says Greenpeace. Available from: http://www.guardian.co.uk/environment/2010/nov/23/indonesia-climate-aid-forests-greenpeace
[16] Ward Anseeuw, Liz Alden Wily, Lorenzo Cotula and Michael Taylor. International Land Council (ILC) 2011. Land rights and the rush for land. Rome
[17] For more information on flex-crops see M. Saturnino et al. 2012. Competing political tendencies in global governance of land grabbing. Transnational Institute
[18] Saturnino M. Borras Jr., Jennifer Franco and Chunyu Wang. December 2012. Competing political tendencies in global governance of land grabbing. Transnational Institute, Agrarian Justice Programme, Discussion paper.
http://www.tni.org/sites/www.tni.org/files/different_responses_to_landgrabbing.pdf
[19] Ruth Kelly, Monique Mikhail, and Marc-Olivier Herman. The Hunger Grains, Oxfam Briefing Paper 161. Oxfam International. 17th September 2012. Available from: http://www.oxfam.org/sites/www.oxfam.org/files/bp161-the-hunger-grains-170912-en.pdf
[20] Achten WMJ, Nielsen LR, Aerts R, Lengkeek AG, Kjær ED, Trabucco A, Hansen JK, Maes WH, Graudal L, Akinnifesi FK, Muys B. (2010) Towards domestication of Jatropha curcas. Biofuels 1(1), 91–107.
[21] John F. McCarthy, Jacqueline A.C. Vel and Suraya Afiff, Trajectories of land acquisition and enclosure: development schemes, virtual land grabs, and green acquisitions in Indonesia’s Outer Islands. The Journal of Peasant Studies Vol. 39, No. 2, April 2012, 521–549
[22] John F. McCarthy, Jacqueline A.C. Vel and Suraya Afiff, As above
[23] Saturnino M. Borras Jr., Jennifer Franco and Chunyu Wang. December 2012. Competing political tendencies in global governance of land grabbing. Transnational Institute Agrarian Justice Programme, Discussion paper.
[24] John F. McCarthy, Jacqueline A.C. Vel and Suraya Afiff, As above
[25] John F. McCarthy, Jacqueline A.C. Vel and Suraya Afiff, As above
[26] See “What kind of land?” box, separate article for discussion on ‘marginal’ land.
[27] Saturnino M. Borras Jr., Jennifer Franco and Chunyu Wang. December 2012. As above.
[28] Caroko, W., Komarudin, H., Obidzinski, K. and Gunarso, P. 2011 Policy and institutional frameworks for
the development of palm oil–based biodiesel in Indonesia. Working Paper 62. CIFOR, Bogor, Indonesia Available from: http://www.cifor.org/publications/pdf_files/WPapers/WP62Komarudin.pdf.